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["Documentation of Wetland Assessment Using ABWRET-A "]
["Site Name:"]
["Investigator Name:"]
["Date of Field Assessment:"]
["Nearest Town:"]
["Latitude (decimal degrees):"]
["Longitude (decimal degrees):"]
["Approximate size of the Assessment Area (AA, in acres)"]
["AA as percent of entire wetland (approx.)"]
["What percent (approx.) of the wetland were you able to visit?"]
["What percent (approx.) of the AA were you able to visit?"]
["Have you attended a training session for this protocol?  If so, indicate approximate month & year."]
["How many wetlands have you assessed previously using this protocol (approx.)?"]
["Comments about the site or this assessment (attach extra page if desired):"]

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["Site Name:                                                                                                                                                          Site Location:"]
["Investigator's Name:                                                                                                                                           Date:"]
["Data Form F.  ABWRET-A. version 1.0.",null,null,null,null,"Data Entry Columns"]
["DIRECTIONS:  Conduct an assessment only after reading the accompanying Manual and explanations on the data forms.  In the Data column, change the 0 (false) to a 1 (true) for the best choice, or for multiple choices where allowed and so indicated.  Answer these questions primarily based on your onsite observations and interpretations.  Do not write in any shaded parts of this data form.  Answering some questions accurately may require conferring with the landowner or other knowledgable persons, and/or reviewing aerial imagery.  Although some conditions can vary greatly by season and from year to year, report only the conditions believed to prevail during the majority of the past 5 years, or if unknown, then the conditions found in the available aerial imagery.",null,null,"Leave Column Blank","Leave Column Blank","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here"]
["#  ","Indicator","Condition Choices"]
["F1","Wetland Type - Predominant","Most of the vegetated part of the AA (wetland Assessment Area) is a (select ONE):",null,null,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0]
["F1.1",null,"Wooded Swamp",null,null,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0]
["F1.2",null,"Bog",null,null,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0]
["F1.3",null,"Fen",null,null,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0]
["F1.4",null,"Marsh or Shallow Open Water",null,null,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0]
["F2","Wetland Types - Subordinate","Mark all other vegetated wetland types in the AA that occupy more than 1 hectare or more than 1% of the vegetated AA.  Do not mark the predominant type again.  If AA is larger than 1 ha, see preliminary imagery-based answer provided by AESRD, but field-verify."]
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[null,null,"Bog",null,null,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0]
[null,null,"Fen",null,null,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0]
[null,null,"Marsh or Shallow Open Water",null,null,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0]
[null,null,"no types other than the predominant one in F1 meet the area threshold.",null,null,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0]
["F3","% Saturated Only","The percentage of the AA that never contains surface water during an average year (that is, except perhaps for a few hours after snowmelt or rainstorms), but which is still a wetland, is:"]
[null,null,"less than 1%, or <0.01 hectare (about 10 m on a side) never has surface water.  In other words, all or nearly all of the AA is inundated permanently or at least seasonally.",null,null,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0]
[null,null,"1-25% of the AA never contains surface water.",null,null,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0]
[null,null,"25-50% of the AA never contains surface water.",null,null,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0]
[null,null,"50-99% of the AA never contains surface water.",null,null,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0]
[null,null,">99% of the AA never contains surface water, except for water flowing in channels and/or in pools that occupy <1% of the AA. SKIP to F26 (Channel Connection & Outflow Duration)",null,null,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0]
[null,null,">99% of the AA never contains surface water, and AA is not intersected by channels that have flow, not even for a few days per year. SKIP to F26.",null,null,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0]
["F4","% with Persistent Surface Water","The percentage of the AA that has surface water (either ponded or flowing, either open or obscured by vegetation) during all of the growing season during most years is:"]
[null,null,"less than 1%, or <0.01 hectare (whichever is less).  SKIP to F8 (% Flooded Only Seasonally).",null,null,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0]
[null,null,"1-25% of the AA, and mostly in narrow channels and/or small scattered pools.",null,null,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0]
[null,null,"1-25% of the AA, and mostly in a single large pool, pond, and/or channel.",null,null,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0]
[null,null,"25-50% of the AA",null,null,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0]
[null,null,"50-95% of the AA",null,null,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0]
[null,null,">95% of the AA",null,null,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0]
["F5","% of Summertime Water That Is Shaded","At mid-day during the warmest time of year, the area of surface water within the AA that is shaded (by emergent or woody vegetation, incised channels, streambanks, or other features also present within the AA) is:"]
[null,null,"<5% of the water is shaded, or no surface water is present then.",null,null,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0]
[null,null,"5-25% of the water is shaded",null,null,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0]
[null,null,"25-50% of the water is shaded",null,null,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0]
[null,null,"50-75% of the water is shaded",null,null,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0]
[null,null,">75% of the water is shaded",null,null,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0]
["F6","Fringe Wetland","If the AA meets the following conditions, it is a fringe wetland: (a) Open water that adjoins the vegetated wetland in a lake, stream, or river during annual low water condition is much wider than the vegetated wetland, and if the AA adjoins a lake (b) the maximum dimension of the lake is greater than 1 km. If true, enter \"1\" and continue.",null,null,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0]
["F7","Lacustrine Wetland","The AA borders a body of ponded open water whose size -- not counting the vegetated AA -- exceeds 8 hectares (about 300 x 300 m) during most of the growing season.  Enter \"1\" if true, \"0\" if false.",null,null,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0]
["F8","% Flooded Only Seasonally","The percentage of the AA that is covered by surface water only during the wettest time of year (and for >2 consecutive days during that time) is:"]
[null,null,"<1%. ",null,null,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0]
[null,null,"1-25% ",null,null,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0]
[null,null,"25-50% ",null,null,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0]
[null,null,"50-95% ",null,null,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0]
[null,null,">95% ",null,null,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0]
["F9","Annual Water Fluctuation Range","The annual fluctuation in surface water level within most of the parts of the AA that contain surface water is:"]
[null,null,"<10 cm change (stable) ",null,null,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0]
[null,null,"10 cm - 50 cm change",null,null,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0]
[null,null,"0.5 - 1 m change",null,null,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0]
[null,null,"1-2 m change",null,null,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0]
[null,null,">2 m change",null,null,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0]
["Is the AA smaller than 0.01 hectare?  If so, enter \"1\" in column D and SKIP TO F23 (Beaver)"]
["F10","Predominant Depth Class","During most of the time when water is present, its depth in most of the area is: [Note: This is not asking for the maximum depth.]"]
[null,null,"<10 cm deep (but >0)",null,null,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0]
[null,null,"10 - 50 cm deep",null,null,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0]
[null,null,"0.5 - 1 m deep",null,null,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0]
[null,null,"1 - 2 m deep",null,null,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0]
[null,null,">2 m deep.  True for many fringe wetlands.",null,null,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0]
["F11","Depth Classes - Evenness of Proportions","When present, surface water in most of the AA usually consists of (select one):"]
[null,null,"One depth class that comprises >90% of the AA’s inundated area (use the classes in the question above).",null,null,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0]
[null,null,"One depth class that comprises 60-90% of the AA's inundated area.",null,null,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0]
[null,null,"Neither of above.  Multiple depth classes; none occupy more than 50% of the AA.",null,null,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0]
["F12","% of Water Ponded vs. Flowing ","The percentage of the AA's surface water that is ponded (stagnant, or flows so slowly that fine sediment is not held in suspension) during most of the time it is present, and which is either open or shaded by emergent vegetation is:"]
[null,null,"<1% or none, or occupies <0.01 hectare cumulatively.  Nearly all water is flowing.  Enter \"1\" and SKIP to F21 (Stained Surface Water).",null,null,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0]
[null,null,"1-5% of the water, and mainly in small pools.  The rest is flowing.",null,null,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0]
[null,null,"1-5% of the water, and mainly in a single large pool or pond.  The rest is flowing.",null,null,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0]
[null,null,"5-30% of the water",null,null,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0]
[null,null,"30-70% of the water",null,null,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0]
[null,null,"70-95% of the water",null,null,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0]
[null,null,">95% of the water.  Little or no visibly flowing water within the AA.",null,null,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0]
["F13","Ponded Open Water - Minimum Size","During most of the growing season, the largest patch of open water that is ponded and is in or bordering the AA is >0.01 hectare (about 10 m by 10 m) and mostly deeper than 0.5 m.  If true enter \"1\" and continue,  If false, enter \"0\" and SKIP to F20 (Floating Algae & Duckweed).",null,null,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0]
["F14","% of Ponded Water That Is Open ","In ducks-eye aerial view, the percentage of the ponded water that is open (lacking emergent vegetation during most of the growing season, and unhidden by a forest or shrub canopy) is:"]
[null,null,"<1% or none, or largest pool occupies <0.01 hectares.  Enter \"1\" and SKIP to F20 (Floating Algae & Duckweed).",null,null,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0]
[null,null,"1-5% of the ponded water.  Enter \"1\" and SKIP to F20.",null,null,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0]
[null,null,"5-30% of the ponded water.",null,null,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0]
[null,null,"30-70% of the ponded water.",null,null,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0]
[null,null,"70-99% of the ponded water.",null,null,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0]
[null,null,"100% of the ponded water. ",null,null,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0]
["F15","Flat Shoreline Extent","The length of the AA's shoreline (along its ponded open water) that is bordered by areas that are nearly flat (a slope less than about 5%) is:"]
[null,null,"<1%",null,null,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0]
[null,null,"1-25%",null,null,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0]
[null,null,"25-50%",null,null,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0]
[null,null,"50-75%",null,null,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0]
[null,null,">75%",null,null,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0]
["F16","Predominant Width of Vegetated Zone within Wetland","At the driest time of year (or lowest water level), the average width of vegetated area in the AA that separates adjoining uplands from open water within the AA is:"]
[null,null,"<1 m",null,null,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0]
[null,null,"1 - 9 m",null,null,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0]
[null,null,"10 - 29 m",null,null,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0]
[null,null,"30 - 49 m",null,null,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0]
[null,null,"50 - 100 m",null,null,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0]
[null,null,"> 100 m",null,null,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0]
["F17","Non-vegetated Aquatic Cover","Near waters that are deeper than 0.5 m, the cover for fish, aquatic invertebrates, and/or amphibians that is provided by horizontally incised banks and/or partly-submerged accumulations of wood thicker than 10 cm (NOT by living vegetation) is:"]
[null,null,"Little or none, or all water is shallower than 0.5 m most of the year.",null,null,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0]
[null,null,"Intermediate",null,null,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0]
[null,null,"Extensive",null,null,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0]
["F18","Interspersion of Robust Emergents & Open Water","During most of the growing season, the spatial pattern of tall robust herbaceous vegetation (e.g., cattail, bulrush) that has surface water beneath it is mostly:"]
[null,null,"Scattered in small clumps, islands, or patches throughout the surface water area.",null,null,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0]
[null,null,"Intermediate",null,null,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0]
[null,null,"Clumped at one or a few sides of the surface water area, or mostly surrounds a central area of open water.  Or such vegetation is absent or covers <9 sq m and <1% of the AA.",null,null,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0]
["F19","Isolated Island","The AA contains (or is part of) an island or beaver lodge within a lake, pond, or river, and is isolated from the shore by water depths >2 m on all sides during an average June.  The island may be solid, or it may be a floating vegetation mat suitable for nesting waterbirds.",null,null,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0]
["F20","Floating Algae & Duckweed","At some time of the year, mats of algae and/or duckweed cover most of the AA's otherwise-unshaded water surface or blanket the underwater substrate.  If true, enter \"1\" in next column.  If untrue or uncertain, enter \"0\".",null,null,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0]
["F21","Stained Surface Water","Most surface water is tea-colored (from tannins, not iron bacteria or silt), and/or its pH is usually <5.5. Nearby vegetation is mostly moss and/or conifers. ",null,null,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0]
["F22","Fish","Fish (native or stocked) are known to be present in the AA.  Or fish can access at least part of the AA during one or more days annually.  If uncertain, use answer from Form OF, item  OF15, or enter \"0\".",null,null,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0]
["F23","Beaver Probability","Use of the AA by beaver during the past 5 years is (select most applicable ONE):"]
[null,null,"evident from direct observation or presence of gnawed limbs, dams, tracks, dens, lodges, or extensive stands of water-killed trees (snags).",null,null,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0]
[null,null,"likely based on known occurrence in the region and proximity to suitable habitat, which may include: (a) a persistent freshwater wetland, pond, or lake, or a perennial low or mid-gradient (<10%) channel, and (b) a corridor or multiple stands of hardwood trees and shrubs in vegetated areas near surface water.",null,null,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0]
[null,null,"unlikely because site characteristics above are deficient, and/or this is a settled area or other area where beaver are routinely removed.  But beaver occur in this part of the region (i.e., within 25 km).",null,null,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0]
[null,null,"none.  Beaver are absent from this part of the region.",null,null,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0]
["F24","Inflow","At least once annually, surface water from a tributary >100m long, or from a larger permanent water body, moves into the AA. It may enter directly in a channel, or as unconfined overflow from a contiguous river or lake, or via a pipe or hardened conduit.   If true, enter 1 and continue.  If false, enter 0 and SKIP to F26 (Channel Connection & Outflow Duration).",null,null,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0]
["F25","Through Flow Pattern","During its travel through the AA at the time of peak annual flow, most of the water arriving in channels [select only the ONE encountered by most of the incoming water]:"]
[null,null,"Does not bump into plant stems as it travels through the AA.  Nearly all the water continues to travel in unvegetated (often incised) channels that have little contact with wetland vegetation, or through a zone of open water such as an instream pond or lake.",null,null,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0]
[null,null,"bumps into herbaceous vegetation but mostly remains in fairly straight channels.",null,null,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0]
[null,null,"bumps into herbaceous vegetation and mostly spreads throughout, or is in widely  meandering, multi-branched, or braided channels.",null,null,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0]
[null,null,"bumps into tree trunks and/or shrub stems but mostly remains in fairly straight channels.",null,null,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0]
[null,null,"bumps into tree trunks and/or shrub stems and follows a fairly indirect path from entrance to exit (meandering, multi-branched, or braided)",null,null,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0]
["F26","Channel Connection & Outflow Duration","The most persistent surface water connection (outlet channel or pipe, ditch, or overbank water exchange) between the AA and the closest off-site downslope water body is:"]
[null,null,"persistent (>9 months/year, including times when frozen)",null,null,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0]
[null,null,"seasonal (14 days to 9 months/year, not necessarily consecutive, including times when frozen)",null,null,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0]
[null,null,"temporary (<14 days, not necessarily consecutive -- must be unfrozen)",null,null,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0]
[null,null,"none -- but maps show a stream or other water body that is downslope from the AA and within a distance that is less than the AA's length.  If so, mark \"1\" here and SKIP TO F28 (Groundwater). ",null,null,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0]
[null,null,"no surface water flows out of the wetland except possibly during extreme events (<once per 10 years). Or, water flows only into a wetland, ditch, or lake that lacks an outlet.  If so, mark \"1\" here and SKIP TO F28 (Groundwater). ",null,null,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0]
["F27","Outflow Confinement","During major runoff events, in the places where surface water exits the AA or connected waters nearby, it:"]
[null,null,"mostly passes through a pipe, culvert, narrowly breached dike, berm, beaver dam, or other partial obstruction (other than natural topography) that does not appear to drain the wetland artificially during most of the growing season.",null,null,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0]
[null,null,"leaves through natural exits (channels or diffuse outflow), not mainly through artificial or temporary features",null,null,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0]
[null,null,"exported more quickly than usual due to ditches or pipes within the AA (or connected to its outlet or within 10 m of the AA's edge) which drain the wetland artificially, or water is pumped out of the AA.",null,null,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0]
["F28","Groundwater: Strength of Evidence","Select first applicable choice. "]
[null,null,"Groundwater monitoring has demonstrated that groundwater primarily discharges to the wetland for longer periods during the year than periods when the wetland recharges the groundwater.  Or, springs are known to be present within the AA.\n\n\n",null,null,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0]
[null,null,"One or more of the following are true: (a) the upper end of the AA is located very close to the base of (but mostly not ON) a natural slope much steeper (usually >15%) than that within the AA and longer than 100 m, OR\n(b) rust deposits (\"iron floc\"), colored precipitates, or dispersible natural oil sheen are prevalent in the AA, OR\n(c) AA water is remarkably clear in contrast to naturally stained waters typical in nearby wetlands, OR\n(d) AA is located at a geologic fault.\n\n",null,null,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0]
[null,null,"Neither of above is true, although some groundwater may discharge to or flow through the AA.  Or groundwater influx is unknown.",null,null,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0]
["F29","Internal Gradient","The gradient along most of the flow path within the AA is:"]
[null,null,"<2%, or, no slope is ever apparent (i.e., flat). Or, the wetland is in a depression or pond with no inlet and no outlet.",null,null,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0]
[null,null,"2-5%",null,null,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0]
[null,null,"6-10%",null,null,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0]
[null,null,">10%",null,null,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0]
["F30","Total Woody Cover -% of the Vegetated AA","Within the entire vegetated part of the AA, the percentage occupied by trees or shrubs taller than 1 m is:"]
[null,null,"<5% of the vegetated AA, or there is no woody vegetation in the AA.  SKIP to F38 (N Fixers)",null,null,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0]
[null,null,"5-25%.  ",null,null,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0]
[null,null,"25-50%",null,null,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0]
[null,null,"50-75%",null,null,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0]
[null,null,">75%",null,null,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0]
["F31","Interspersion of Herbaceous and Woody Cover","The following best represents the distribution pattern of woody vegetation VS. unshaded herbaceous/ moss vegetation within the AA:"]
[null,null,"(a) Woody cover and herbaceous/ moss cover EACH comprise 30-70% of the vegetated part of the AA, AND (b) There are many patches of woody vegetation scattered widely within herbaceous/ moss vegetation, or many patches of herbaceous vegetation scattered widely within woody vegetation.",null,null,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0]
[null,null,"(a) Woody cover and herbaceous/ moss EACH comprise 30-70% of the vegetated AA, AND (b) There are few patches (\"islands\") of woody vegetation scattered widely within herbaceous vegetation, or few patches of herbaceous/ moss vegetation (\"gaps\") scattered widely within woody vegetation.",null,null,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0]
[null,null,"(a) Woody cover OR herbaceous/ moss comprise >70% of the vegetated AA, AND (b) There are several patches of the other scattered within it. ",null,null,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0]
[null,null,"(a) Woody cover OR herbaceous/ moss comprise >70% of the vegetated AA, AND (b) The other is absent or is mostly in a single area or distinct zone with almost no intermixing of woody and unshaded herbaceous/ moss vegetation.",null,null,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0]
["F32","Tall Woody Canopy- % of the Vegetated AA","Within the vegetated part of the AA, just the woody plants taller than 3 m occupy:"]
[null,null,"<1% of the vegetated AA, or the AA lacks trees.  Enter \"1\" and SKIP to F35 (Exposed Shrub).",null,null,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0]
[null,null,"1-25% of the vegetated AA",null,null,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0]
[null,null,"25-50% of the vegetated AA",null,null,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0]
[null,null,"50-95% of the vegetated AA",null,null,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0]
[null,null,">95% of the vegetated part of the AA",null,null,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0]
["F33","Woody Diameter Classes","Mark all the classes of woody plants within the AA, but only IF they comprise more than 5% of the woody canopy within the AA.  Do not count trees that adjoin but are not within the AA."]
[null,null,"coniferous, 1-9 cm diameter and >1 m tall",null,null,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0]
[null,null,"broad-leaved deciduous 1-9 cm diameter and >1 m tall",null,null,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0]
[null,null,"coniferous, 10-19 cm diameter",null,null,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0]
[null,null,"broad-leaved deciduous 10-19 cm diameter",null,null,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0]
[null,null,"coniferous, 20-40 cm diameter",null,null,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0]
[null,null,"broad-leaved deciduous 20-40 cm diameter",null,null,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0]
[null,null,"coniferous, >40 cm diameter",null,null,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0]
[null,null,"broad-leaved deciduous >40 cm diameter",null,null,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0]
["F34","Downed Wood","The number of downed wood pieces longer than 2 m and with diameter >10 cm, and not persistently submerged, is:"]
[null,null,"Several ( >5 if AA is >5 hectares, less for smaller AAs)",null,null,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0]
[null,null,"Few or none ",null,null,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0]
["F35","Exposed Shrub Canopy","Woody vegetation 1 to 3 m tall that is not under the drip line of taller woody vegetation comprises:"]
[null,null,"<5% of the vegetated AA and (if a fringe wetland) <5% of its water edge.  Or <0.01 hectare.  SKIP to F38 (N Fixers).",null,null,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0]
[null,null,"5-25% of the vegetated AA or (if a fringe wetland) 5-25% of the water edge  -- whichever is greater.",null,null,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0]
[null,null,"25-50% of the vegetated AA or the water edge, whichever is greater. ",null,null,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0]
[null,null,"50-95% of the vegetated AA or the water edge, whichever is greater.",null,null,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0]
[null,null,">95% of the vegetated part of the AA or the water edge, whichever is greater.",null,null,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0]
["F36","Dominance of Most Abundant Shrub Species ","Determine which two native shrub species (1 to 3 m tall) comprise the greatest portion of the native shrub cover.  Then choose one of the following:"]
[null,null,"those species together comprise > 50% of the areal cover of native shrub species.",null,null,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0]
[null,null,"those species together do not comprise > 50% of the areal cover of native shrub species.",null,null,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0]
["F37","Broad-leaved Deciduous Trees and Shrubs","The percentage of the AA's tree or shrub cover that is broad-leaved deciduous and is taller than 1 meter is:"]
[null,null,"<1%, or largest patch occupies less than 0.01 hectare",null,null,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0]
[null,null,"1-25% of the tree or shrub cover (whichever has more)",null,null,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0]
[null,null,"25-50% of the tree or shrub cover (whichever has more)",null,null,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0]
[null,null,"50-75% of the tree or shrub cover (whichever has more)",null,null,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0]
[null,null,">75% of the tree or shrub cover (whichever has more)",null,null,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0]
["F38","N Fixers","The percent of the AA's shrub plus ground cover that is nitrogen-fixing plants (e.g., alder, baltic (wire) rush, sweetgale, lupine, clover, other legumes) is:"]
[null,null,"<1% or none",null,null,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0]
[null,null,"1-25% of the shrub plus ground cover, in the AA or along its water edge (whichever has more).",null,null,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0]
[null,null,"25-50% of the shrub plus ground cover, in the AA or along its water edge (whichever has more).",null,null,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0]
[null,null,"50-75% of the shrub plus ground cover, in the AA or along its water edge (whichever has more).",null,null,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0]
[null,null,">75% of the shrub plus ground cover, in the AA or along its water edge (whichever has more).",null,null,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0]
["F39","Snags","The number of large snags (diameter >20 cm) in the AA plus the upland area within 10 m of the wetland edge is:"]
[null,null,"Several ( >2/hectare) and a pond, lake, or slow-flowing water wider than 10 m is within 1 km.",null,null,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0]
[null,null,"Several ( >2/hectare) but above not true.",null,null,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0]
[null,null,"Few or none ",null,null,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0]
["F40","Moss Extent","Within the part of the AA that lacks persistent surface water, the cover of moss is:"]
[null,null,"<5% of the ground cover",null,null,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0]
[null,null,"5-25% of the ground cover",null,null,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0]
[null,null,"25-50% of the ground cover",null,null,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0]
[null,null,"50-95% of the ground cover",null,null,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0]
[null,null,">95% of the ground cover",null,null,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0]
["F41","% Bare Ground & Thatch","Consider the parts of the AA that lack surface water at the driest time of the growing season.  Viewed from directly above the ground layer, the predominant condition in those areas at that time is:"]
[null,null,"Little or no (<5%) bare ground is visible between erect stems or under canopy anywhere in the vegetated AA. Ground is extensively blanketed by dense thatch, moss, lichens, graminoids with great stem densities, or plants with ground-hugging foliage. ",null,null,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0]
[null,null,"Slightly bare ground (5-20% bare between plants) is visible in places, but those areas comprise less than 5% of the unflooded parts of the AA.",null,null,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0]
[null,null,"Much bare ground (20-50% bare between plants) is visible in places, and those areas comprise more than 5% of the unflooded parts of the AA. ",null,null,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0]
[null,null,"Other conditions",null,null,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0]
[null,null,"Not applicable.  Surface water (either open or obscured by emergent plants) covers all of the AA all the time.",null,null,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0]
["F42","Ground Irregularity","Consider the parts of the AA that lack surface water at some time of the year.  Excluding slash from logging, the number of small pits, raised mounds, hummocks, boulders, upturned trees, animal burrows, gullies, natural levees, wide soil cracks, and microdepressions is:"]
[null,null,"Few or none (minimal microtopography; <1% of that area) ",null,null,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0]
[null,null,"Intermediate",null,null,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0]
[null,null,"Several (extensive micro-topography)",null,null,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0]
["F43","Upland Inclusions","Within the AA, inclusions of upland that individually are >100 sq.m. are:"]
[null,null,"Few or none",null,null,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0]
[null,null,"Intermediate (1 - 10% of vegetated part of the AA).",null,null,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0]
[null,null,"Many (e.g., wetland-upland \"mosaic\", >10% of the vegetated AA).",null,null,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0]
["F44","Soil Texture","In parts of the AA that lack persistent water, the texture of soil in the uppermost layer is mostly:  [To determine this, use a trowel to check in at least 3 widely spaced locations, and use the soil texture key in Appendix A of the Manual]"]
[null,null,"Loamy: includes loam, sandy loam",null,null,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0]
[null,null,"Fines: includes silt, glacial flour, clay, clay loam, silty clay, silty clay loam, sandy clay, sandy clay loam.",null,null,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0]
[null,null,"Organic",null,null,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0]
[null,null,"Coarse: includes sand, loamy sand, gravel, cobble, stones, boulders, fluvents, fluvaquents, riverwash.",null,null,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0]
["F45","Shorebird Feeding Habitats","During any 2 consecutive weeks of the growing season, the extent of mudflats, bare unshaded saturated areas not covered by thatch, and unshaded non-acidic waters shallower than 6 cm (see definition in column E) is:"]
[null,null,"none, or <100 sq. m within the AA.",null,null,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0]
[null,null,"100-1000 sq. m within the AA.",null,null,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0]
[null,null,"1000 – 10,000 sq. m within the AA.",null,null,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0]
[null,null,">10,000 sq. m within the AA.",null,null,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0]
["F46","Herbaceous - Percent of Vegetated Wetland","In aerial (\"ducks eye\") view, the maximum annual cover of dense herbaceous vegetation (graminoids + forbs, but not mosses and submerged and floating aquatics) is:"]
[null,null,"<5% of the vegetated part of the AA (excluding parts that are moss-covered or beneath shrubs or trees), or <0.01 hectare (whichever is less).  Mark \"1\" here and SKIP to F50 (Invasive Plant Cover).",null,null,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0]
[null,null,"5-25% of the vegetated AA.",null,null,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0]
[null,null,"25-50% of the vegetated AA.",null,null,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0]
[null,null,"50-95% of the vegetated AA.",null,null,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0]
[null,null,">95% of the vegetated AA.",null,null,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0]
["F47","Forb Cover","The areal cover of forbs reaches an annual maximum of:"]
[null,null,"<5% of the herbaceous & moss cover",null,null,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0]
[null,null,"5-25% of the herbaceous & moss cover",null,null,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0]
[null,null,"25-50% of the herbaceous & moss cover",null,null,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0]
[null,null,"50-95% of the herbaceous & moss cover",null,null,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0]
[null,null,">95% of the herbaceous & moss cover. SKIP to F50 (Invasive Plant Cover).",null,null,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0]
["F48","Sedge Cover","Sedges (Carex spp.) and/or cottongrass (Eriophorum spp.) occupy:"]
[null,null,"<5% of the herbaceous cover, or <0.01 hectare",null,null,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0]
[null,null,"5-50% of the herbaceous cover",null,null,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0]
[null,null,"50-95% of the herbaceous cover",null,null,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0]
[null,null,">95% of the herbaceous cover",null,null,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0]
["F49","Dominance of Most Abundant Herbaceous Species ","Determine which two native herbaceous (forb and graminoid) species comprise the greatest portion of the herbaceous cover that is unshaded by a woody canopy.  Then choose one of the following:"]
[null,null,"those species together comprise > 50% of the areal cover of native herbaceous plants at any time during the year.",null,null,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0]
[null,null,"those species together do not comprise > 50% of the areal cover of native herbaceous plants at any time during the year.",null,null,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0]
["F50","Invasive Plant Cover","In central Alberta, common invasive graminoids include smooth brome, most bluegrasses, quackgrass, timothy, alfalfa, reed canarygrass, red fescue, spreading bentgrass.  Common invasive forbs include most thistles and sow-thistles, most clovers, sweetclover, black medick, dandelion, great plantain, hemp-nettle, lamb's-quarters, shepherd's-purse, curly dock, pennycress, wallflower, hawksbeard, tansy, chickweed, sticky-willy bedstraw, stickseed, tall buttercup. Select first applicable choice:"]
[null,null,"invasive or other non-native species appear to be absent in the AA, or are present only in trace amount (a few individuals)",null,null,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0]
[null,null,"Invasive species are present in more than trace amounts, but comprise <5% of herbaceous cover (or woody cover, if the invasives are woody).",null,null,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0]
[null,null,"Invasive species comprise 5-20% of the herb cover.",null,null,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0]
[null,null,"Invasive species comprise 20-50% of the herb cover.",null,null,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0]
[null,null,"Invasive species comprise >50% of the herb cover.",null,null,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0]
["F51","Weed Source Along Edge","Along the wetland-upland boundary, the percent of the upland edge (within 3 m of wetland) that is occupied by plant species that are considered invasive (see above) is:"]
[null,null,"none of the upland edge (invasives apparently absent)",null,null,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0]
[null,null,"some (but <5%) of the upland edge",null,null,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0]
[null,null,"5-50% of the upland edge",null,null,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0]
[null,null,"most (>50%) of the upland edge",null,null,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0]
["F52","Natural Cover in Buffer","Along the wetland-upland edge and extending 30 m upslope, the percentage of the upland that contains natural (not necessarily native -- see column E) land cover taller than 10 cm is:"]
[null,null,"<5% ",null,null,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0]
[null,null,"5 to 30%",null,null,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0]
[null,null,"30 to 60%",null,null,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0]
[null,null,"60 to 90%",null,null,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0]
[null,null,">90%.  SKIP to F54 (Cliffs).",null,null,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0]
["F53","Type of Cover in Buffer","Within 30 m upslope of the wetland-upland edge closest to the AA, the upland land cover that is NOT unmanaged vegetation or water is mostly (mark ONE):"]
[null,null,"impervious surface, e.g., paved road, parking lot, building, exposed rock.",null,null,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0]
[null,null,"bare or nearly bare pervious surface or managed vegetation, e.g., lawn, annual crops, mostly-unvegetated clearcut, landslide, unpaved road, dike.",null,null,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0]
["F54","Cliffs, Steep Banks, or Salt Lick ","In the AA or within 100 m, there is a known salt lick, or elevated terrestrial features such as cliffs, talus slopes, stream banks, or excavated pits (but not riprap) that extend at least 2 m nearly vertically, are unvegetated, and potentially contain crevices or other substrate suitable for nesting or den areas.  Enter 1 (yes) or 0 (no).",null,null,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0]
["F55","New Wetland","The AA is (or is within, or contains) a \"new\" wetland resulting from human actions (e.g., excavation, impoundment) or debris flows,  or other factors affecting what once was upland (non-hydric) soil."]
[null,null,"No",null,null,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0]
[null,null,"yes, and created 20 - 100 years ago ",null,null,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0]
[null,null,"yes, and created 3-20 years ago",null,null,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0]
[null,null,"yes, and created within last 3 years",null,null,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0]
[null,null,"yes, but time of origin unknown",null,null,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0]
[null,null,"unknown if new within 20 years or not",null,null,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0]
["F56","Visibility","From the best vantage point on public roads, public parking lots, public buildings, or well-defined public trails that intersect, adjoin, or are within 100 m of the wetland, some part of the wetland is (select best case):"]
[null,null,"easily visible",null,null,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0]
[null,null,"somewhat visible",null,null,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0]
[null,null,"barely or not visible",null,null,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0]
["F57","Ownership","Most of the AA is (select one):"]
[null,null,"publicly owned conservation lands that exclude new timber harvest, roads, mineral extraction, and intensive summer recreation (e.g., off-road vehicles).  Includes most Protected Lands.",null,null,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0]
[null,null,"publicly owned resource use lands (allowed activities such as timber harvest, mining, or intensive recreation), or unknown.  Includes most Crown Reservations/Notations.",null,null,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0]
[null,null,"Owned by non-profit conservation organization or lease holder who allows public access.",null,null,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0]
[null,null,"Other private ownership, including First Nations.",null,null,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0]
["F58","Non-consumptive Uses - Actual or Potential","Assuming access permission was granted, select ALL statements that are true of the AA as it currently exists:"]
[null,null,"For an average person, walking is physically possible in (not just near) >5% of the AA during most of the growing season, e.g., free of deep water and dense shrub thickets.",null,null,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0]
[null,null,"Maintained roads, parking areas, or foot-trails are within 10 m of the AA, or the AA can be accessed part of the year by boats arriving via contiguous waters.",null,null,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0]
[null,null,"Within or near the AA, there is an interpretive center, trails with interpretive signs or brochures, and/or regular guided interpretive tours. ",null,null,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0]
[null,null,"The AA contains or adjoins a public boat dock or ramp, or is within 1 km of a campground, picnic area, or winter sports park.",null,null,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0]
["F59","Unvisited Core Area ","The percentage of the AA almost never visited by humans during an average growing season probably comprises: [Note: Do not include visitors on trails outside of the AA unless more than half the wetland is visible from the trails and they are within 30 m of the wetland edge.  In that case, imagine the percentage of the AA that would be covered by the trail if it were placed within the AA.]"]
[null,null,"<5% and no inhabited building is within 100 m of the AA",null,null,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0]
[null,null,"<5% and inhabited building is within 100 m of the AA",null,null,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0]
[null,null,"5-50% and no inhabited building is within 100 m of the AA",null,null,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0]
[null,null,"5-50% and inhabited building is within 100 m of the AA",null,null,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0]
[null,null,"50-95%",null,null,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0]
[null,null,">95% of the AA",null,null,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0]
["F60","Frequently Visited Area","The percentage of the AA visited by humans almost daily for several weeks during an average growing season probably comprises: [Note: Do not include visitors on trails outside of the AA unless more than half the wetland is visible from the trails and they are within 30 m of the wetland edge.   In that case, imagine the percentage of the AA that would be covered by the trail if it were placed within the AA.]"]
[null,null,"<5%.  If F59 was answered \">95%\", SKIP to F63 (Consumptive Uses).",null,null,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0]
[null,null,"5-50%",null,null,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0]
[null,null,"50-95%",null,null,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0]
[null,null,">95% of the AA",null,null,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0]
["F61","BMP - Soils","Boardwalks, paved trails, fences or other infrastructure and/or well-enforced regulations appear to effectively prevent visitors from walking on soils within nearly all of the AA when they are unfrozen.  Enter \"1\" if true.",null,null,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0]
["F62","BMP - Wildlife Protection","Fences, observation blinds, platforms, paved trails, exclusion periods, and/or well-enforced prohibitions on motorized boats, off-leash pets, and off road vehicles appear to effectively exclude or divert visitors and their pets from the AA at critical times in order to minimize disturbance of wildlife (except during hunting seasons).  Enter \"1\" if true. ",null,null,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0]
["F63","Consumptive Uses (Provisioning Services)","Recent evidence was found within the AA of the following potentially-sustainable consumptive uses.  Select all that apply."]
[null,null,"Low-impact commercial timber harvest (e.g., selective thinning)",null,null,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0]
[null,null,"Extraction of surface water without noticeably affecting surface water area, depth, or persistence.",null,null,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0]
[null,null,"Grazing by livestock",null,null,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0]
[null,null,"Harvesting of native plants, native hay, or mushrooms (observed or known, not assumed)",null,null,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0]
[null,null,"Hunting (observed or known, not assumed)",null,null,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0]
[null,null,"Furbearer trapping",null,null,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0]
[null,null,"Fishing (observed or known, not assumed)",null,null,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0]
[null,null,"No evidence of any of the above",null,null,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0]
["F64","Domestic Wells","The closest wells or water bodies that currently provide drinking water are:"]
[null,null,"Within 100 m of the AA",null,null,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0]
[null,null,"100-500 m away",null,null,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0]
[null,null,">500 m away, or no information",null,null,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0]
["F65","Salinity, Alkalinity, Conductance ","Based on measurement from a surface water area larger than .01 hectare, the AA's surface water is mostly:"]
[null,null,"Brackish or saline (conductance of >25 mS/cm, or >5000 ppm TDS). Or plants that indicate saline conditions comprise >20% of ground cover.  Trees and shrubs mostly absent.  Salt crust obvious around the perimeter and on flats.",null,null,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0]
[null,null,"Slightly brackish (conductance of 2.5- 25 mS/cm, or 500 - 5000 ppm TDS).  Or plants that indicate saline conditions comprise 1-20% of ground cover.  Salt crust may or may not be present along perimeter.",null,null,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0]
[null,null,"Fresh (conductance of < 2.5 mS/cm, or <500 ppm TDS). Plants that indicate saline conditions are sparse or absent. No salt crust along perimeter.",null,null,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0]
[null,null,"Unknown condition (was not measured because surface water absent or insufficient, or measurement conflicted with plant indicators). ",null,null,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0]
["F66","Water Quality Problem Area Located Upslope","Sampling indicates problems with the quality of surface waters or sediment within the AA, or within 5 km upstream or upslope, as caused by (enter 1 for ALL that apply):"]
[null,null,"nutrients (phosphorus, nitrate, ammonia), or a water body within 5 km that contributes to the AA has been labeled \"hyper-eutrophic\" based on excessive levels of either total phosphorus or chlorophyll-a.",null,null,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0]
[null,null,"suspended sediment or turbidity",null,null,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0]
[null,null,"metals (mercury, lead, zinc, copper, cadmium, others)",null,null,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0]
[null,null,"petrochemicals (pesticides, herbicides, PCBs, others)",null,null,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0]
[null,null,"None of above, or no data. ",null,null,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0]
["F67","Prior Investment in the AA","Mark ALL of the following that apply to this AA:"]
[null,null,"Regulatory Investment: The AA is all or part of a mitigation site used explicitly to offset impacts elsewhere",null,null,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0]
[null,null,"Non-regulatory Investment: The AA is part of or contiguous to a wetland on which public or private organizational funds were spent to preserve, create, restore, enhance, the wetland (excluding mitigation wetlands)",null,null,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0]
[null,null,"Sustained Scientific Use: Plants, animals, or water in the AA have been monitored for >2 years, unrelated to any regulatory requirements, and data are available to the public.  Or the AA is part of an area that has been designated by an agency or institution as a benchmark, reference, or status-trends monitoring area.",null,null,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0]
[null,null,"None of the above, or no information for any.",null,null,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0]
["F68","Wetland as a % of Its Contributing Area (Catchment)","View the approximate boundaries of the wetland's catchment (CA) as shown in the map AESRD provides in response to your data request.  Then adjust those boundaries if necessary based on your field observations of the surrounding terrain, and/or by using procedures described in the ABWRET Manual. Relative to the extent of this catchment (but excluding the area of the AA), this AA and any bordering waters together comprise (select ONE):"]
[null,null,"<1% of their catchment",null,null,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0]
[null,null,"1 to 10% of their catchment",null,null,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0]
[null,null,"10 to 100%  of their catchment",null,null,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0]
[null,null,"Larger than the area of their catchment (wetland has essentially no catchment, e.g., isolated by dikes with no input channels, or is a raised bog). ",null,null,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0]
["F69","Plants or Animals of Conservation Concern","If required, survey the AA for plant or animal species believed to be of conservation concern in Alberta (see list on Form F in Appendix A of Manual).  Do so at appropriate times of the year, especially if the data review conducted during the office phase of this assessment indicated their past presence in the general vicinity.  If you do detect these species or have reliable knowledge of their recent (within ~5 years) occurrence within the AA, indicate that below.  "]
[null,null,"One or more of the rare plant species was detected within the AA (Appendix A, Table A.4).",null,null,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0]
[null,null,"One or more of the rare fish species was detected within the AA.",null,null,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0]
[null,null,"One or more of the rare amphibian species was detected within the AA.",null,null,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0]
[null,null,"One or more of the rare waterbird species was detected within the AA.",null,null,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0]
[null,null,"One or more of the rare songbird or mammal species was detected within the AA.",null,null,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0]
[null,null,"None of the above, or no data.",null,null,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0]
["F70","Size of AA","The AA's size (in hectares) was measured as the following (next column):"]
[null,null,"If this (or a corrected measurement) is GREATER than 10 hectares enter a \"1\" here:"]

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["Site Name and Location:",null,null,"Investigator:","Date:"]
["Data Form S (Stressors).  ABWRET-A version 1.0.",null,null,null,null,"Leave Column Blank","Leave Column Blank","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here","Enter site ID here"]
["S5","Altered Timing of Water Inputs"]
[null,"In the last column, place a check mark next to any item that is likely to have caused the timing of water inputs (but not necessarily their volume) to shift by hours, days, or weeks, becoming either more muted (smaller or less frequent peaks spread over longer times, more temporal homogeneity of flow or water levels) or more flashy (larger or more frequent spikes but over shorter times).  [FR, INV, PH, STR]"]
[null,"   flow regulation in tributaries or water level regulation in adjoining water body, or other control structure at water entry points that regulates inflow to the wetland"]
[null,"   snow storage areas that drain directly to the wetland"]
[null,"   increased pavement and other impervious surface in the CA"]
[null,"   straightening, ditching, dredging, and/or lining of tributary channels in the CA"]
[null,"If any items were checked above, then for each row of the table below, you may assign points.  However, if you believe the checked items had no measurable effect on the timing of water conditions in any part of the AA, then leave the \"0's\" for the scores in the following rows.  To estimate effects, contrast the current condition with the condition if the checked items never occurred or were no longer present. "]
[null,null,"Severe (3 pts)","Medium (2 points)","Mild (1 point)"]
[null,"Spatial extent within the wetland of timing shift ",">95% of wetland ","5-95% of wetland ","<5% of wetland ",0,null,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0]
[null,"When most of the timing shift began","<3 yrs ago","3-9 yrs ago ","10-100 yrs ago",0,null,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0]
[null,"  Score the following 2 rows only if the altered inputs began within past 10 years, and only for the part of the wetland that experiences those."]
[null,"Input timing now vs. previously","shift of weeks","shift of days","shift of hours or minutes",0,null,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0]
[null,"Flashiness or muting","became very flashy or controlled","intermediate","became mildly flashy or controlled",0,null,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0]
[null,"Sum=",null,null,null,{"$f":"SUM(F11:F15)","v":0},null,{"$f":"SUM(H11:H15)","v":0},{"$f":"SUM(I11:I15)","v":0},0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,{"$f":"SUM(BU11:BU15)","v":0},0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,{"$f":"SUM(EG11:EG15)","v":0},0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,{"$f":"SUM(GS11:GS15)","v":0},0,0,0,0,0,0,0,0,0,0,0,0,0,0]
[null,null,null,null,"Stressor Subscore=",{"$f":"F16/12","v":0},null,{"$f":"H16/12","v":0},{"$f":"I16/12","v":0},0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,{"$f":"BU16/12","v":0},0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,{"$f":"EG16/12","v":0},0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,{"$f":"GS16/12","v":0},0,0,0,0,0,0,0,0,0,0,0,0,0,0]
["S6","Accelerated Inputs of Contaminants and/or Salts"]
[null,"In the last column, place a check mark next to any item -- occurring in either the wetland or its CA -- that is likely to have accelerated the inputs of contaminants or salts to the AA.  [NRv, PRv, STR]"]
[null,"   stormwater or wastewater effluent (including failing septic systems), landfills, industrial facilities"]
[null,"   road salt"]
[null,"   metals & chemical wastes from mining, shooting ranges, snow storage areas, oil/ gas extraction, other sources"]
[null,"   oil or chemical spills (not just chronic inputs) from nearby roads"]
[null,"  artificial drainage or erosion of contaminated or saline soils"]
[null,"  pesticides, as applied to lawns, croplands, roadsides, or other areas in the CA"]
[null,"If any items were checked above, then for each row of the table below, you may assign points.  However, if you believe the checked items did not cumulatively expose the AA to significantly higher levels of contaminants and/or salts, then leave the \"0's\" for the scores in the following rows.  To estimate effects, contrast the current condition with the condition if the checked items never occurred or were no longer present. "]
[null,null,"Severe (3 points)","Medium (2 points)","Mild (1 point)"]
[null,"Usual toxicity of most toxic contaminants","industrial effluent, metals mine, or AA is cropped (& sprayed) annually","crops in catchment but not in AA, fossil fuel extraction or pipeline, power station","mildly impacting (e.g., residential/ commercial)",0,null,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0]
[null,"Frequency & duration of input","frequent and year-round","frequent but mostly seasonal","infrequent & during high runoff events mainly",0,null,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0]
[null,"AA proximity to main sources (actual or potential)","0 - 15 m","15-100 m or in groundwater","in more distant part of contributing area",0,null,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0]
[null,"Sum=",null,null,null,{"$f":"SUM(F28:F30)","v":0},null,{"$f":"SUM(H28:H30)","v":0},{"$f":"SUM(I28:I30)","v":0},0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,{"$f":"SUM(BU28:BU30)","v":0},0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,{"$f":"SUM(EG28:EG30)","v":0},0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,{"$f":"SUM(GS28:GS30)","v":0},0,0,0,0,0,0,0,0,0,0,0,0,0,0]
[null,null,null,null,"Stressor Subscore=",{"$f":"F31/9","v":0},null,{"$f":"H31/9","v":0},{"$f":"I31/9","v":0},0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,{"$f":"BU31/9","v":0},0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,{"$f":"EG31/9","v":0},0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,{"$f":"GS31/9","v":0},0,0,0,0,0,0,0,0,0,0,0,0,0,0]
["S7","Accelerated Inputs of Nutrients"]
[null,"In the last column, place a check mark next to any item -- occurring in either the wetland or its CA -- that is likely to have accelerated the inputs of nutrients to the wetland.  [STR]"]
[null,"   stormwater or wastewater effluent (including failing septic systems), landfills"]
[null,"   fertilizers applied to lawns, ag lands, or other areas in the CA"]
[null,"   livestock, dogs  "]
[null,"   artificial drainage of upslope lands"]
[null,"If any items were checked above, then for each row of the table below, you may assign points.  However, if you believe the checked items did not cumulatively expose the AA to significantly more nutrients, then leave the \"0's\" for the scores in the following rows.  To estimate effects, contrast the current condition with the condition if the checked items never occurred or were no longer present. "]
[null,null,"Severe (3 points)","Medium (2 points)","Mild (1 point)"]
[null,"Type of loading","high density of unmaintained septic, confined feedlot operation","moderate density septic, cropland, secondary wastewater treatment plant","livestock, pets, low density residential",0,null,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0]
[null,"Frequency & duration of input","frequent and year-round","frequent but mostly seasonal","infrequent & during high runoff events mainly",0,null,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0]
[null,"AA proximity to main sources (actual or potential)","0 - 15 m","15-100 m","in more distant part of contributing area",0,null,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0]
[null,"Sum=",null,null,null,{"$f":"SUM(F41:F43)","v":0},null,{"$f":"SUM(H41:H43)","v":0},{"$f":"SUM(I41:I43)","v":0},0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,{"$f":"SUM(BU41:BU43)","v":0},0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,{"$f":"SUM(EG41:EG43)","v":0},0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,{"$f":"SUM(GS41:GS43)","v":0},0,0,0,0,0,0,0,0,0,0,0,0,0,0]
[null,null,null,null,"Stressor Subscore=",{"$f":"F44/9","v":0},null,{"$f":"H44/9","v":0},{"$f":"I44/9","v":0},0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,{"$f":"BU44/9","v":0},0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,{"$f":"EG44/9","v":0},0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,{"$f":"GS44/9","v":0},0,0,0,0,0,0,0,0,0,0,0,0,0,0]
["S8","Excessive Sediment Loading from Contributing Area"]
[null,"In the last column, place a check mark next to any item present in the CA that is likely to have elevated the load of waterborne or windborne sediment reaching the wetland from its CA.  [INV, SRv, STR]"]
[null,"   erosion from plowed fields, fill, timber harvest, dirt roads, vegetation clearing, fires"]
[null,"   erosion from construction, in-channel machinery in the CA "]
[null,"   erosion from off-road vehicles in the CA"]
[null,"   erosion from livestock or foot traffic in the CA"]
[null,"   stormwater or wastewater effluent"]
[null,"   sediment from road sanding, gravel mining, other mining, oil/ gas extraction"]
[null,"   accelerated channel downcutting or headcutting of tributaries due to altered land use"]
[null,"   other human-related disturbances within the CA"]
[null,"If any items were checked above, then for each row of the table below, you may assign points (3, 2, or 1 as shown in header) in the last column.  However, if you believe the checked items did not cumulatively add significantly more sediment or suspended solids to the AA, then leave the \"0's\" for the scores in the following rows.  To estimate effects, contrast the current condition with the condition if the checked items never occurred or were no longer present. "]
[null,null,"Severe (3 points)","Medium (2 points)","Mild (1 point)"]
[null,"Erosion in CA","extensive evidence, high intensity*","potentially (based on high-intensity* land use) or scattered evidence","potentially (based on low-intensity* land use) with little or no direct evidence",0,null,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0]
[null,"Recentness of significant soil disturbance in the CA","current & ongoing","1-12 months ago",">1 yr ago",0,null,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0]
[null,"Duration of sediment inputs to the wetland","frequent and year-round","frequent but mostly seasonal","infrequent & during high runoff events mainly",0,null,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0]
[null,"AA proximity to actual or potential sources","0 - 15 m, or farther but on steep erodible slopes","15-100 m or in groundwater","in more distant part of contributing area",0,null,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0]
[null,"* high-intensity= extensive off-road vehicle use, plowing, grading, excavation, erosion with or without veg removal;  low-intensity= veg removal only with little or no apparent erosion or disturbance of soil or sediment",null,null,"Sum=",{"$f":"SUM(F58:F61)","v":0},null,{"$f":"SUM(H58:H61)","v":0},{"$f":"SUM(I58:I61)","v":0},0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,{"$f":"SUM(BU58:BU61)","v":0},0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,{"$f":"SUM(EG58:EG61)","v":0},0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,{"$f":"SUM(GS58:GS61)","v":0},0,0,0,0,0,0,0,0,0,0,0,0,0,0]
[null,null,null,null,"Stressor Subscore=",{"$f":"F62/12","v":0},null,{"$f":"H62/12","v":0},{"$f":"I62/12","v":0},0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,{"$f":"BU62/12","v":0},0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,{"$f":"EG62/12","v":0},0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,{"$f":"GS62/12","v":0},0,0,0,0,0,0,0,0,0,0,0,0,0,0]
["S9","Soil or Sediment Alteration Within the Assessment Area"]
[null,"In the last column, place a check mark next to any item present in the wetland that is likely to have compacted, eroded, or otherwise altered the wetland's soil.  If the AA is a created or restored wetland or pond, exclude those actions.  [CS, INV, NR, PH, STR]"]
[null,"   compaction from machinery, off-road vehicles, or mountain bikes, especially during wetter periods"]
[null,"   leveling or other grading not to the natural contour"]
[null,"   tillage, plowing (but excluding disking for enhancement of native plants)"]
[null,"   fill or riprap, excluding small amounts of upland soils containing organic amendments (compost, etc.) or small amounts of topsoil imported from another wetland"]
[null,"   excavation"]
[null,"   ditch cleaning or dredging in or adjacent to the wetland"]
[null,"   boat traffic in or adjacent to the wetland and sufficient to cause shore erosion or stir bottom sediments"]
[null,"   artificial water level or flow manipulations sufficient to cause erosion or stir bottom sediments"]
[null,"If any items were checked above, then for each row of the table below, you may assign points.  However, if you believe the checked items did not measurably alter the soil structure and/or topography, then leave the \"0's\" for the scores in the following rows.  To estimate effects, contrast the current condition with the condition if the checked items never occurred or were no longer present. "]
[null,null,"Severe (3 points)","Medium (2 points)","Mild (1 point)"]
[null,"Spatial extent of altered soil",">95% of wetland or >95% of  its upland edge (if any)","5-95% of wetland or 5-95% of its upland edge (if any)","<5% of wetland and <5% of its upland edge (if any)",0,null,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0]
[null,"Recentness of significant soil alteration in wetland","current & ongoing","1-12 months ago",">1 yr ago",0,null,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0]
[null,"Duration","long-lasting, minimal veg recovery","long-lasting but mostly revegetated","short-term, revegetated, not intense ",0,null,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0]
[null,"Timing of soil alteration","frequent and year-round","frequent but mostly seasonal","infrequent & mainly during scattered or one-time events",0,null,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0]
[null,"Sum=",null,null,null,{"$f":"SUM(F76:F79)","v":0},null,{"$f":"SUM(H76:H79)","v":0},{"$f":"SUM(I76:I79)","v":0},0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,{"$f":"SUM(BU76:BU79)","v":0},0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,{"$f":"SUM(EG76:EG79)","v":0},0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,{"$f":"SUM(GS76:GS79)","v":0},0,0,0,0,0,0,0,0,0,0,0,0,0,0]
[null,null,null,null,"Stressor Subscore=",{"$f":"F80/12","v":0},null,{"$f":"H80/12","v":0},{"$f":"I80/12","v":0},0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,{"$f":"BU80/12","v":0},0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,{"$f":"EG80/12","v":0},0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,{"$f":"GS80/12","v":0},0,0,0,0,0,0,0,0,0,0,0,0,0,0]

{"sheet":"OF","index":3,"n_rows":74,"n_cols":6,"rows_kept":74,"cut":false,"hidden":false,"merged":[]}
["#","Code","Indicator",null,null,"Notes"]
["OF1","AquifVul","Aquifer Vulnerability Index ",null,null,"Raw values range from 1 (low) to 6 based on surficial geology and depth to aquifer.  From Ag Land Resource Atlas of Alberta."]
["OF2","Aspect","Aspect of the AA's 100m Upslope Buffer",null,null,"Aspect within +/- 45 degrees of north gets a 1, Aspect within +/- 45 degrees of sourth gets a 0, all others get a 0.5.  From the DEM."]
["OF3","BioDivZone","Key Wildlife Biodiversity Zone",null,null,"1 (yes) or 0 (no).  Layer from ESRD 2010, minimum resolvable unit is 0.02 ha."]
["OF4","ChanConn","Channel Connection",null,null,"1 (yes) or 0 (no) based only on available hydrography layer."]
["OF5","ClassRich1k","Wetland Class Richness Within 1km",null,null,"Number of mapped wetland classes within 1 km of wetland centroid.  From Alberta Merged Wetland Inventory map layer."]
["OF6","ClassRichIn","Wetland Class Richness Within Wetland",null,null,"Number of mapped wetland classes within the wetland. From Alberta Merged Wetland Inventory map layer."]
["OF7","Dist2DevCrop","Distance to Nearest Annual Cropland or Developed Land",null,null,"All distances >5 km are considered to be in the 100th percentile.  From AAFC \"Annual Crop\" and \"Developed\" map layers."]
["OF8","Dist2Road","Distance to Nearest Road (from Wetland Edge)",null,null,"All distances >5 km are considered to be in the 100th percentile."]
["OF9","DistPop","Distance to Nearest Well-settled Area",null,null,"All distances >5 km are considered to be in the 100th percentile.  \"Well settled\" = ESRD Geoadministrative Cities, Towns, Villages, Summer Villages."]
["OF10","DuckDens","Waterfowl Breeding Density",null,null,"Mean Waterfowl Count per ha, by survey segment from the WBPBHS_Strata layer of US Fish & Wildlife Service. Minimum resolvable unit = 20,166 ha."]
["OF11","ElevPctileHUC8","Elevation Percentile Within HUC8 ",null,null,"Calculated as (wetland's elevation - minimum elevation of wetland's HUC8) divided by elevation range (max-min) of the wetland's HUC8."]
["OF12","FenBogMarsh","% of the Wetland that is Fen Bog or Marsh",null,null,"The percentages of these 3 classes were summed within each wetland, then the percentile of that sum as calculated for all wetlands in RWAU was determined and used as reference point.  From Alberta Merged Wetland Inventory map layer."]
["OF13","FenMarshSwamp","% of the Wetland that is Fen Marsh or Swamp",null,null,"The percentages of these 3 classes were summed within each wetland, then the percentile of that sum as calculated for all wetlands in RWAU was determined and used as reference point.  From Alberta Merged Wetland Inventory map layer."]
["OF14","FenPct","% of the Wetland that is Fen",null,null,"From Alberta Merged Wetland Inventory map layer."]
["OF15","FishPres","Fish Presence",null,null,"1 (yes) or 0 (no). Based only on Class A or B designation (Alberta Water Act Codes of Practice streams) layer from GOA 2013."]
["OF16","Fringe","Fringe Wetland",null,null,"1 (yes) or 0 (no) based on a join of the target wetland's centroid with intersecting lake layer from base hydrography features, plus spatial join of target wetland with intersecting river polygon layer from that layer.  From Alberta Merged Wetland Inventory map layer."]
["OF17","GrowDD","Growing Degree Days",null,null,"Based on Canadian Forest Service average number of days above 5C during growing season 1971-2000, minimum resolution of 1 km2."]
["OF18","GWDspring","Groundwater Discharge Area or Spring",null,null,"1 (yes) or 0 (no). Discharge predicted by ESRD Clean Energy Policy Branch from 2000 SRDM 60m DEM & Water Well Information Database."]
["OF19","HistList","Alberta Culture Listing of Historic Resources",null,null,"1 (yes) or 0 (no).  Wetland centroid intersects a listed site (2014 list)."]
["OF20","IBirdArea","Important Bird Area",null,null,"1 (yes) or 0 (no) based on official designation."]
["OF21","Lake","Lacustrine Wetland",null,null,"1 (yes) or 0 (no) based on size >8 ha."]
["OF22","LGIndex","L/G Index (Residence Time)",null,null,"If wetland size <10 ha, then =NULL (ignored in calculations). Otherwise, ratio of flow length to gradient, both measured within the wetland.  Measured from Alberta Merged Wetland Inventory map layer."]
["OF23","MarshPct","% of the AA that is Marsh",null,null,"From Alberta Merged Wetland Inventory map layer."]
["OF24","MarshUniq","MarshPct/ MarshPct1k",null,null,"From Alberta Merged Wetland Inventory map layer."]
["OF25","MarshFenSwamp","MarshPct + FenPct + SwampPct",null,null,"From Alberta Merged Wetland Inventory map layer."]
["OF26","MixHerbWood","Interspersion Index for Internal Herbaceous & Woody Vegetation (macroscale)",null,null,"If wetland size <10 ha, then =NULL (ignored in calculations). Otherwise calculated as the number of swamp or forested polygons within each wetland and normalizing the number by the ratio of the total area of those polygons to the wetland's total area."]
["OF27","MixWaterVeg","Interspersion Index for Internal Water & Vegetation (macroscale)",null,null,"If wetland size <10 ha, then =NULL (ignored in calculations). Otherwise calculated as the number of open water polygons within each wetland and normalizing the number by the ratio of the total area of those polygons to the wetland's total area."]
["OF28","NatCov1k","% Natural Cover within 1km",null,null," \"Natural Cover\" includes all AAFC classes except Water, Annual Crops, Exposed Land, & Developed."]
["OF29","OWarea","Open Water Area ",null,null,"From Alberta Merged Wetland Inventory map layer."]
["OF30","OWpct ","% of AA that is Open Water (macro scale)",null,null,"From Alberta Merged Wetland Inventory map layer."]
["OF31","OWpct_INV","% of AA that is Open Water (macro scale, Invertebrate Habitat)",null,null,"Instead of RWAU percentile, for the Invertebrate Habitat function the raw value is converted to a score as follows: <1%=0.2;  1%-5%=0.6; 6-30%=0.8, 31-70%=1; 71-99%=0.4; >99%=0.  From Alberta Merged Wetland Inventory map layer."]
["OF32","OWpct_AM","% of AA that is Open Water (macro scale, Amphibian Habitat)",null,null,"Instead of RWAU percentile, for the Amphibian Habitat function the raw value is converted to a score as follows: <1%=0.2;  1%-99%=1.0; >99%=0.  From Alberta Merged Wetland Inventory map layer."]
["OF33","OWpct_WB","% of AA that is Open Water (macro scale, Waterbird Habitat)",null,null,"Instead of RWAU percentile, for the Invertebrate Habitat function the raw value is converted to a score as follows: <1%=0;  1%-5%=0.4; 6-30%=0.8, 31-70%=1; 71-99%=0.6; >99%=0.2.  From Alberta Merged Wetland Inventory map layer."]
["OF34","PerimNatCov","% of Wetland Perimeter Adjoined by Natural Cover",null,null," \"Natural Cover\" includes all AAFC classes except Water, Annual Crops, Exposed Land, & Developed.  Measured around wetland boundary as depiced in Alberta Merged Wetland Inventory map layer."]
["OF35","PPET","Climate Moisture Surplus (P-PET)",null,null,"Annual precipitation minus evapotranspiration. Based on Canadian Forest Service average precip and ET during growing season 1971-2000, minimum resolution of 1 km2. "]
["OF36","Public","Ownership category = Public",null,null,"1 (yes) or 0 (no)"]
["OF37","RaptorNest","Sensitive Raptor Nesting Area",null,null,"1 (yes) or 0 (no).  From FWMIS database."]
["OF38","RareBirdUse","Nesting Bird Colony, Piping Plover Water Body, or Trumpeter Swan Use Area",null,null,"1 (yes) or 0 (no) wetland centroid intersects the merged Colonial Nesting Bird, Piping Plover Water Body and Trumpeter Swan layers from FWMIS database."]
["OF39","RarePlantRange","Rare Plant Range",null,null,"1 (yes) or 0 (no) an ACIMS-designated rare plant is in the same township as the wetland"]
["OF40","RdDens1k","Road Density in 1km Buffer"]
["OF41","Reserve","Ecological Reserve or Natural Area ",null,null,"1 (yes) or 0 (no)"]
["OF42","RipFloodpl","Riparian or Floodway Location",null,null,"1 (yes) or 0 (no) based on flood hazard (floodways and flood fringes) from ESRD River Forecast Section and merged with lotic riparian area layer (ESRD 2011, 0.02 ha minimum revolvable unit)."]
["OF43","SBstaging","Shorebird Staging Wetland ",null,null,"1 (yes) or 0 (no) based on WHSRN Shorebird Staging Area layer"]
["OF44","SensAm","Within Range of a Sensitive Amphibian",null,null,"1 (yes) or 0 (no).  From FWMIS map layer."]
["OF45","SlopeBuffer","% Slope ",null,null,"Measured within 100m radius of Wetland Centroid"]
["OF46","SoilOrgPct","Organic Soil Content (macroscale)",null,null,"AGRASID used for RWAUs 14, 15, 16 and 17, GSC used for remaining RWVAUs.   Minimum resolvable unit is 1 ha."]
["OF47","SoilTex_WS","Soil Texture (macroscale)",null,null,"see Table 1. AGRASID 4.0 used for RWAUs 14, 15, 16 and 17, GSC used for remaining RWAUs. Minimum resolvable unit is 1 ha."]
["OF48","SoilTex_PR","Soil Texture (macroscale)",null,null,"see Table 2. AGRASID used for RWAUs 14, 15, 16 and 17, GSC used for remaining RWAUs.  Minimum resolvable unit is 1 ha."]
["OF49","SoilTex_NROE","Soil Texture (macroscale)",null,null,"see Table 3. AGRASID used for RWAUs 14, 15, 16 and 17, GSC used for remaining RWAUs.  Minimum resolvable unit is 1 ha."]
["OF50","Spring","Springs within 300m",null,null,"1 (yes) or 0 (no) from AGS Energy Resources Conservation Board."]
["OF51","Sub0Days","Subzero Days"]
["OF52","SwampMarshPct","Swamp + Marsh as % of the Wetland",null,null,"The percentages of these 2 classes were summed within each wetland, then the percentile of that sum as calculated for all wetlands in RWVAU was determined and used as reference point.  From Alberta Merged Wetland Inventory map layer."]
["OF53","Trail","Access to Trail Network",null,null,"1 (yes) or 0 (no) mapped trail present within 100m of wetland centroid"]
["OF54","TrumSwan","Trumpeter Swan Area",null,null,"1 (yes) or 0 (no) from FWMIS database."]
["OF55","UndevOpenL1k","% Undeveloped Openlands Within 1km",null,null,"AAFC layer"]
["OF56","UniqClass","Local Uniqueness of Wetland's Class",null,null,"MAX of: (UniqFen, UniqMarsh, UniqBog, UniqSwamp). From Alberta Merged Wetland Inventory map layer."]
["OF57","UniqFenMarsh","FenMarshPct/ FenMarshPct1k",null,null,"From Alberta Merged Wetland Inventory map layer."]
["OF58","UniqFenMarshSwamp","FenSwampMarshPct/ FenSwampMarshPct1k",null,null,"From Alberta Merged Wetland Inventory map layer."]
["OF59","VegCon1k","Vegetation Connectivity to Other Wetlands within 1 km",null,null,"1 (yes) or 0 (no) natural cover intersects both the target wetland and another wetland within 1 km. From Alberta Merged Wetland Inventory map layer.  Natural cover derived from AAFC layers."]
["OF60","WatProb","Water Permanence Probability",null,null,"Percent probability of surface water being present, as calculated by Creed et al. (2014 unpublished)"]
["OF61","WBstaging","Waterfowl Staging Wetland",null,null,"1 (yes) or 0 (no) based on AESA criteria #2"]
["OF62","WetArea","AA Size",null,null,"From Alberta Merged Wetland Inventory map layer."]
["OF63","WetDens1k","Wetland Density Within 1km",null,null,"From Alberta Merged Wetland Inventory map layer."]
["OF64","WetDens1k_NoBog","Wetland Density Within 1km (excluding bogs)",null,null,"From Alberta Merged Wetland Inventory map layer."]
["OF65","WetDens1k_OW","Wetland Density Within 1km (excluding those with no open water)",null,null,"From Alberta Merged Wetland Inventory map layer."]
["OF66","WetPctHUC8","Wetland as a % of Its HUC8",null,null,"From Alberta Merged Wetland Inventory map layer."]
["OF67","WetPerim2Area","Perimeter-Area Ratio",null,null,"From Alberta Merged Wetland Inventory map layer."]
["OF68","WetVegArea","Wetland Vegetated Area",null,null,"same as WetArea minus OWarea"]
["OF69","WetWooded","% of Wetland Classified as Swamp or Forested (macro scale)",null,null,"Join of Swamps class in Alberta Merged Wetland Inventory map layer with AAFC Forest layers, divided by WetArea."]
["OF70","WindSumm","Wind Energy - Summer",null,null,"Windspeed at 30m above land surface in summer, average for years 1958-2000.  Minimum resolvable unit is 2500 ha. Incomplete data coverage for RWVAUs 15 and 21.  From Environment Canada."]
["OF71","WindWin","Wind Energy - Winter ",null,null,"Windspeed at 30m above land surface in winter, average for years 1958-2000.  Minimum resolvable unit is 2500 ha. Incomplete data coverage for RWVAUs 15 and 21. From Environment Canada."]
["OF72","WQrisk","Surface Water Quality Risk Index",null,null,"Raw values potentially range from 1 (low) to 6 and are based on coarse-scale per-unit-area estimates of manure production and fertiliser and pesticide use as of 2001. From Agricultural Land Resource Atlas of Alberta."]
["OF73","RWVAU","RWVAU"]

{"sheet":"AllSitesA","index":4,"n_rows":56,"n_cols":1,"rows_kept":56,"cut":false,"hidden":false,"merged":[]}
["Function (ABWRET-A raw score)"]
["Surface Water Storage (WS)"]
["Stream Flow Support (SFS)"]
["Streamwater Cooling (WC)"]
["Sediment & Toxicant Retention & Stabilization (SR)"]
["Phosphorus Retention (PR)"]
["Nitrate Removal & Retention (NR)"]
["Organic Nutrient Export (OE)"]
["Fish Habitat (FH)"]
["Aquatic Invertebrate Habitat (INV)"]
["Amphibian Habitat (AM)"]
["Waterbird Habitat (WB)"]
["Songbird, Raptor, & Mammal Habitat (SBM)"]
["Pollinator & Native Plant Habitat (PH)"]
["Human Use & Recognition (HU)"]
[]
[]
["Normalized Function Scores (ABWRET-A):"]
["Surface Water Storage (WS)"]
["Stream Flow Support (SFS)"]
["Streamwater Cooling (WC)"]
["Sediment & Toxicant Retention & Stabilization (SR)"]
["Phosphorus Retention (PR)"]
["Nitrate Removal & Retention (NR)"]
["Organic Nutrient Export (OE)"]
["Fish Habitat (FH)"]
["Aquatic Invertebrate Habitat (INV)"]
["Amphibian Habitat (AM)"]
["Waterbird Habitat (WB)"]
["Songbird, Raptor, & Mammal Habitat (SBM)"]
["Pollinator & Native Plant Habitat (PH)"]
["Human Use & Recognition (HU)"]
[]
[]
["Normalized  (ABWRET_A) Based on 175 Calibrated Sites"]
["Hydrological Health (HH)"]
["Water Quality (WQ)"]
["Ecological Health (EH)"]
["Human Use (HU)"]
["RWVAU #"]
["Value Score (ABWRET_a)"]
["Value Category (a, b, c, d)"]
["Abundance Factor"]
["Final Score(A, B, C, D)"]
[]
[]
["Normalized Score (ABWRET_A) Based on Wetlands in RWVAU"]
["Hydrological Health (HH)"]
["Water Quality (WQ)"]
["Ecological Health (EH)"]
["Human Use (HU)"]
["RWVAU #"]
["Value Score (ABWRET_a)"]
["Value Category (a, b, c, d)"]
["Abundance Factor"]
["Final Score(A, B, C, D)"]

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["Phosphorus Retention (PR)",10,10,10,10,10,10,10,10,4.4901487416666663,10,10,4.4986076475000001,6.9965553674999992,6.9791708358333331,10,10,10,10,10,10,10,10,4.5610442999999998,10,4.33951419,4.1082030245833332,10,10,4.3720444187499998,10,4.0933047500000006,5.0408168441666668,10,10,10,3.4050672795833337,4.2792592404166667,10,2.2996363766666668,10,10,5.1696040374999992,3.28038425,10,2.3807334816666668,2.6777442591666665,10,7.5714312479166672,4.4592391712500001,4.5400168983333336,5.1669152549999993,6.0927998733333331,10,2.9896546674999995,7.1562988616666683,10,10,10,10,10,6.054340008333333,1.93728758,4.3507238527777776,10,8.5382363199999993,5.5039990883333338,10,10,4.2169009074999995,2.88949935625,10,10,10,3.0535612895833331,10,2.7398942179166665,4.6202362041666669,3.819904255,3.3448095541666669,5.2431239262500009,5.5667502075000002,10,10,1.7198025275000002,4.5207117525000005,3.176015819166667,10,10,10,10,10,2.6306613150000002,4.9043457850000003,3.2770270774999997,10,10,10,10,10,5.9073560374999996,3.7000115583333333,4.6005438154166667,4.6215170079166672,4.8608992141666665,3.8507398283333334,4.9939395733333338,10,4.7201117858333328,3.5168592116666666,10,3.4446524233333333,4.0359673224999995,6.3951594720833338,2.7393237424999999,3.077678578888889,10,10,4.9007703245833341,7.1391443304166664,4.6223773295833332,2.0276005758333335,4.0675516070833337,10,4.9137763854166669,10,10,5.5621495595833341,10,3.102241705,1.7246523733333332,10,5.3959125166666668,5.4507393225000005,4.9560322770833327,2.5085820537500005,3.8878348770833333,10,10,10,4.0154971383333331,4.5572301074999997,4.0526494916666671,3.4463055111111114,3.1685855479166669,3.6725290058333337,10,10,10,2.6262003545833332,10,4.0830888700000001,10,10,10,4.7596753808333334,3.5888976895833338,10,6.035479916249999,5.4382131724999994,10,10,7.2886924079166686,10,6.9624015729166651,2.2526522037500003,4.6180597066666662,10,10,1.7307636104166662,10,3.0973381454166669,3.9149724074999996,10,4.3172076633333329,10]
["Nitrate Removal & Retention (NR)",2.0140191116666664,2.5145924942857141,4.9656178683333332,3.9209376312500006,2.852443618214286,1.6714059545833335,3.6876831828571435,4.8092380196428577,3.693031585,3.6561161057142852,2.3824590010714286,2.6093090596428574,4.0585398635714283,4.0882088242857142,2.0913394954166669,3.3123729967857147,4.4433351042857145,2.3279962374999998,2.1601743304166665,1.9104696616666663,2.9519222271428576,3.4804913120833336,2.8067331935714286,2.27140365625,2.9205844303571427,1.4349005495833334,3.2001292495833331,2.1455266662500003,3.1941481696428573,2.0322115585714284,3.3623269596428567,2.9697472846428576,3.5199155058333331,1.9294395470833334,3.2219836425000006,2.1217938679166668,2.821875286428571,1.837930706666667,2.7027262010714286,4.1510003221428571,3.6127263814285717,5.2070909778571419,4.4708918158333333,2.9428125054166658,3.4563363162499998,2.4813943912499998,1.7181781339285715,5.5103252725000011,3.2059563975000001,1.8906281439285713,1.5856343225,4.5249122839285718,2.7674489216666665,3.9006893489285717,3.7946864357142864,2.9827003300000001,4.494403592916667,2.3494727310714287,3.3563614720833335,4.4957588208333341,3.7362052260714282,2.3722472389285714,2.8674476545833332,2.5961560600000002,5.229279067857143,3.6004896878571429,2.8409210107142857,4.6698541279166665,2.9175670703571432,1.9628197321428573,3.393272620416667,1.6105556189285712,3.335507239583333,4.4645407182142858,3.7416393774999994,2.8553900953571434,2.4681240517857144,1.7240593900000001,3.0220952985714291,3.3745485907142863,4.080784425,4.8943343941666662,4.253090423571428,1.6390025199999996,2.7894737582142861,2.3690405432142856,3.8175204012500004,4.1761034245833333,4.7014584900000003,4.3628542139285713,3.4352578983333331,4.6942358221428568,4.352342498214286,2.9294540428571429,3.6699852367857142,2.3762512025000002,2.0766785791666664,1.8237382085714284,2.2199982199999999,4.0319770975000004,3.4046260246428566,2.763729162142857,4.3688045385714283,3.2893586353571429,2.8878262612499999,2.7679859446428572,3.2199105800000001,2.8095818453571431,2.2652227300000001,3.3132609458333335,4.0514908671428573,5.3525062982142853,4.7961197967857148,3.6331880079166661,3.0309534720833335,4.9947582308333338,3.1573893139285718,4.2258175057142857,4.7419338478571422,3.6313501953571423,3.0047699142857143,5.1368311660714285,2.2567100316666666,3.5123474270833333,5.0543999683333327,2.6286439174999998,4.5817926616666664,3.9648235116666664,3.0377166857142863,2.7376025737499998,1.786012500833333,4.4451273514285718,2.4461884875000002,2.1902937321428571,4.453958665,3.7185908021428569,3.1524720320833333,3.6039135033333336,5.306562426428572,2.9001833692857151,2.0549230450000002,2.4279683014285718,5.0592214789999996,4.4821364837499997,3.4321193446428571,2.4261214421428572,2.4104158471428567,3.7184399867857145,5.1163963254166669,1.5368537795833335,2.012516180714286,2.8998735941666665,3.2802018174999996,2.6638327049999999,3.921713949285714,3.6130724460714285,5.6068148595833334,3.5789043782142853,3.6713582271428575,4.2744729560714285,2.5286199800000002,3.9417013185714289,3.805430385357143,4.1658513139285711,2.977323001785714,1.8250378110714285,3.1776989183333333,4.3134574003571426,3.1213172521428572,2.8199103517857145,2.775835110714286,2.1429328191666666,2.9226579035714284,2.75880212625,1.9139469675]
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["Songbird, Raptor, & Mammal Habitat (SBM)",5.6003310237499999,5.4567228251388897,5.5961739352777773,5.1497000716666665,4.8730238962499994,4.2663798012500003,4.5294163369444442,4.6052465372222224,5.3359951918055559,6.5549580586111125,6.2145073579166663,5.7662398706944442,5.2198974918055558,7.0655946080555552,5.7379916893055549,4.7181935923611107,6.7514475718055555,5.517181018194445,4.3014640730555556,4.1905592688888893,5.3465850797222227,6.6760887222222234,7.352801854861112,5.6456944650000009,6.7423842008333335,6.640492563194444,6.7819051805555564,5.8965429883333345,4.8720948087500009,4.4784355823611115,7.7193417774999995,5.5527390018055556,6.0655121695833341,4.1778003650000004,4.2526409123611115,5.0838028740277776,6.1460226658333337,6.117143136527778,5.6574838119444451,3.9824341365277771,7.0439422669444438,5.3026715127777777,5.425996363055555,4.2643246841666667,5.1060450198611109,5.5755502506944445,5.7800710779166673,5.9304122506944443,6.0437749347222223,5.4562857604166659,5.061909561805555,6.0779482884722222,3.9113907806944441,6.0791762786111114,6.0507612427777779,4.4058292036111109,6.0968617427777776,4.7590280963888896,4.6949824173611114,5.4233389362500004,6.204360812777777,5.5362033048611101,4.2858072802777771,4.1405148190277776,5.4451883530555554,5.1548879809722212,5.0418196861111122,4.4796013016666665,4.5753751245833332,5.1594089631944442,4.0680015115277781,4.5570961669444445,5.4705555894444435,6.5888714216666671,4.8988908541666669,6.4778547679166651,6.547909189305555,4.2325006980555555,6.6622656723611122,6.2649880822222217,5.8829186004166658,5.051664889305556,5.2603131452777783,6.6495523134722223,5.2738389808333332,5.3059764448611126,4.6476615194444442,4.5638765663888892,5.0368937019444449,5.3269743137500001,4.4414308126388891,4.565225134305555,7.871541955833333,7.3262825249999999,4.370256490277777,4.1200325622222227,4.2666437690277776,5.5625622233333338,5.3997775849999998,6.4071531619444446,5.6362209118055562,4.9852637265277782,7.104301266805555,7.0610653269444432,4.9673272105555561,5.785526626527778,3.9440671291666662,5.1502784379166675,5.3072275712500003,4.5966211845833334,5.3931672487500002,6.888515005833332,6.3442691934722228,5.125544029305555,6.0328260680555568,4.9694362961111116,6.8888367890277777,4.7885457544444447,6.5631302300000005,6.8747950302777774,6.8242082169444451,6.866062325972222,5.4598252098611111,7.6229711827777766,5.9816464247222232,4.9358320649999996,4.7158920494444452,4.7101935273611124,6.3745674913888895,6.9074704827777778,4.4409901045833333,5.1971014193055556,6.6262261359722228,6.2600788691666667,6.4219751850000009,5.8206202581944444,5.7250921851388892,4.7402447370833327,6.8883582641666665,5.1363231826388889,5.5930843554166678,5.005998698611112,5.5229140656944429,4.9347298249999998,3.647200493472222,7.2059025290277781,6.8286431694444438,5.5435985108333341,6.2894759008333336,6.0514432651388894,6.7840159513888896,5.7748289500000007,4.3592247226388885,5.916823090555555,5.37579031875,5.0059418844444448,5.6576024733333332,5.9121174544444441,7.4070407511111114,5.8498374391666665,3.487968728611111,4.4413886984722222,5.1256889458333337,5.6217535099999996,5.7463227987499996,6.7694675238888893,4.2242372705555562,5.3192945511111116,6.9668985440277762,3.8391254399999997,7.4230576477777763,6.3922668580555548,4.7779857205555558,4.5636918450000001,4.680858134027778]
["Pollinator & Native Plant Habitat (PH)",4.541467293277778,4.2867380460833342,5.1352884069722213,5.0187071765000004,4.6317808596388881,4.1168715867222225,4.3988468478055562,4.3519901207222222,4.631319193805556,5.9332361103611113,5.4259081908055551,5.4706528336944444,4.8147639931388895,6.170811085444444,5.3654039814722223,3.8983632099166665,6.2490006529999995,4.5870766903611111,3.5292571298611115,3.3332289881666672,4.1765042374166672,5.8319145382222226,6.3430344686666675,4.472475629222223,5.3202450401666654,5.5272763440277783,5.8191969366666676,4.6796704903888902,4.0736003074722227,5.8124782092777769,6.1921518688333332,4.6896246430000001,4.8572598892222221,3.4704399819444443,3.5218474535277777,4.5556255856944441,5.5502054642222216,5.2159129433055549,5.1808827404444449,3.2162228546944442,6.2580964265000008,6.2565789866944446,4.0990675866388893,3.7620449220277781,5.2102713653055552,4.74821982925,5.0677860087777784,5.6554083195555549,7.4890516790555548,4.4661298006944445,4.2989130563055555,5.1659052888611114,3.1369776641388887,6.6636607023611107,5.4995125186388893,3.7569656896944448,5.868467220277779,4.1785193091944457,4.0993952355000003,4.5628054458888894,5.2657408179166669,4.794644646888889,3.7319832118888892,3.7571141583888883,4.989742607777778,5.0965890352777778,4.5441994228333336,4.4898235389722219,4.1821613233888888,4.1561471859166659,3.9235545291944445,4.0922464639444449,5.0511035957222212,6.229019779722222,5.0701195460555546,5.9414401380277768,5.8836625090277783,3.7202557062222223,5.6944409174166672,4.8453584498333342,4.6449453522499997,6.4034212840833336,4.5731870984722223,5.8308729578611107,4.4285575861944446,4.9016692169722225,4.7808920231666665,4.4293168903888889,5.2556263853888883,4.5252161784166667,3.7731793668055551,3.697178955638889,6.8702310253888887,7.9573209432500001,4.4395191599444441,4.0539156501388893,4.0941211841111107,4.5940001940000004,4.5421355622222226,5.3581457754999997,5.373795426888889,4.8137258983611106,6.9861263286944428,6.3071726355277766,4.8135923270555558,5.4743914476666671,3.626871792222222,4.5561607978333329,4.908374824638889,4.3641560480833332,4.4083187458611111,6.1483600277500008,6.1134687371111109,4.4199522526944452,5.674489500361112,6.5178752796666659,6.8280574474444444,4.7266610228055566,6.1730181458055551,6.1937829445555561,5.9295105112777788,6.6938284564722226,4.6629393538888895,6.2306182233888894,6.8819612735555555,4.1761132378611103,4.4316336768888887,4.1471969845555554,5.6106357948333327,6.2491153488333326,4.299134230611112,4.6051306837777775,5.8771802660833341,5.6178124697222218,5.7400776970000003,4.6460303845833328,5.0859926903611106,6.0776970879722212,6.5595231292777783,4.9311179758611106,5.2900635388333326,4.3710778989999994,4.6979437807222215,4.2051907161111108,2.886473983138889,6.7670728768333346,6.1585793971111116,4.8819158343888898,6.0676930383888887,4.7725576556944453,7.9074756516666653,5.7568636565555567,5.9468004396944449,5.9693196905555554,4.4562584914166674,3.615645270166667,5.1904506451111123,4.9325370839999998,7.229628391166667,5.4040761930555545,3.3000730218333336,4.6490853157222229,4.5597391017777769,4.4537188382777781,5.4166074359166663,6.2269803493888887,3.554861995888889,4.9492062970277777,5.9078821272500006,3.8873128750555552,6.6992825103888887,5.1614935348333333,4.151315818194445,4.3884434469999993,4.2025468743333336]
["Human Use & Recognition (HU)",1.1044678986250001,6.3488398195000002,1.4071287757499999,1.1977185295000001,1.4176493990000001,1.4094560298750001,6.1696496447500007,5.9936349880000002,5.2302323158750008,4.0644243163749998,4.13197151425,5.2223640912500002,5.9630257283749994,4.7531731893750004,1.2268076806250001,4.0509536496249998,4.6161046350000001,7.2465221624999998,1.8380424979999999,1.6421176153750001,2.0622088600000001,3.2794009136250004,0.85540746487499997,1.0987983617499999,1.739442110625,1.3707544847499997,1.444185032,1.8184159583749997,1.80647681075,5.8178332130000001,4.6232200885000001,3.0906450537499994,1.26412656225,2.3969901281250001,4.9640056149999996,1.8901420306249999,5.2991075247499992,1.478599882625,4.9291325492499993,6.1652060926249996,3.6159751363750003,8.0776073453750001,5.0782895444999996,7.2821565562500004,7.4973077156250003,5.1816636982499995,6.9470041961249995,5.4682595818750004,4.4577719442500001,1.9154654581249999,5.0495206173749994,4.205829783375,1.7979124712500001,7.4623666352499995,7.8438449712500002,1.7756910390000002,3.5626593771250006,5.7218558776249999,5.5621627435000001,4.0339827526249996,6.3750279496250002,4.7929284266250001,5.1032147731249999,4.3200328312499998,5.6879877168749999,6.0476257906250002,4.6298962701249993,3.911394321625,4.4109205787500008,5.7286204125000006,4.5576415028749997,4.7116087936250004,4.0133398732500005,4.6726952930000003,4.0483337067500003,8.1682851186250005,4.9773513084999994,3.747971884,4.069186604375,5.1373805074999996,4.195436123625,3.6673228121249997,5.0970738835000002,8.5681033908749988,1.5219207201250002,2.2909821297499997,4.6084740936250004,4.596724815,3.6497595193749999,5.1009289786250003,4.8749232637499995,5.0478641898749999,5.5747819013750002,5.665533629375,2.518609181875,1.8574692002500002,1.301963539125,1.7415365008750001,1.1641631167499999,3.7593888283750005,5.9354450107499996,5.2804274021249995,4.1798154806249999,4.2786598940000005,4.3949091235000006,6.1677535661250005,5.0081172568749999,1.9408130134999999,4.3953943200000003,0.99082152187499994,4.3205718414999996,4.7038990333749995,5.5383348535000003,5.8920887539999995,6.4357226081249994,4.2816153648749999,4.3857324482500006,7.9636609561250005,5.458118025500001,5.0136750226249998,4.535576361375,4.0835891541250007,2.0339664501249999,1.5704436873750001,7.0272788153750003,7.0130732396250011,5.1146569470000003,1.804382792625,1.0914968732499999,6.371142050125,4.6640499807499998,4.7051826579999991,3.1751704543749999,3.8199728109999995,5.8631302882499998,4.5117857418749994,6.2834196171250003,3.6487517995000003,1.5118118858749998,4.4532567895000001,4.4865260441250001,6.8033864821250001,2.5537888959999999,6.5810996826250001,3.4933059654999998,4.7641420642499996,4.6810639705000003,3.8460366414999996,0.74711518975000002,1.6858700835000002,3.3970760171249998,1.3625895744999998,4.4330831848749996,3.6792316918750001,2.3820899093749999,2.0513237105000002,3.59122443475,4.4580271836250001,4.4613508028749997,3.2426395558749999,1.1194432434999999,7.2479133778749993,6.458537051875,5.2689716660000006,4.0660795537500007,4.3415341386250006,3.9452065832500005,5.1188557882500003,4.8391300373749999,1.3083361681249999,6.2043831357499997,3.45898828775,3.146437824875,6.2233130821249993,5.6408976233749994]
[]
[]
["Function (ABWRET-E ) Normalized:","CD194","GADS1","HANS","MACL","RAUS","RAUS3","MIQUEL01","MIQUEL02","MIQUEL23","MIQUEL36","MLPP10","MIQUEL03","MLPPN","MLPPS","MINHWY","MNSTSE","05CD195","05FAJJColl","05CD89","05FC10","05FC200","05FC13","05FC25","05FC30","HOLM","MITT","MITTEA","MARUS8","CURR",189590,5257,3042,3185,5321,11912,6919,7111,305377,209695,753655,2803,1039,1232,37882,92831,148287,196557,"3042BS",20031,23420,23467,23669,12,52,19555,25411,644242,5062,282535,4507,4647,272004,6926,436864,15082,15434,15186,17152,6174,228332,17902,588706,11568,11491,421060,11488,11698,421953,423143,10763,11808,368499,3410,286841,495717,22720,715354,715420,728347,8245,321809,359454,2882,205184,18237,488834,586891,692585,693500,708592,22645,2939,2966,872,3350,2137,5824,16930,6846,6786,25368,40430,2658,57,4104,14076,841,3014,2944,2953,1828,177552,"05CD90","MITTEA2",6497,1340,23929,25577,662856,444845,505036,13871,421244,636534,421050,20957,309237,368504,206100,1094,10576,7544,34259,99916,166,840,842,107527,25701,"MARUNE",25256,752362,753469,421057,"DALY",148810,23981,738519,752536,2778,11537,191518,186633,21071,421059,6920,"05CD67",15949,212872,208930,842121,735360,"SUMM",7374,3934]
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[]
[]
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["Final Score(A, B, C, D)","B","A","A","B","A","A","A","A","D","A","A","D","B","A","A","A","A","A","A","A","B","A","D","B","D","D","A","A","D","A","D","D","A","A","A","D","D","B","D","A","A","A","D","A","C","D","A","A","D","D","D","D","B","C","A","B","A","B","A","B","C","D","D","B","A","D","B","B","D","D","A","C","B","D","C","D","D","D","D","D","C","A","B","D","D","D","B","B","C","A","B","D","A","C","A","B","A","C","C","D","D","D","D","D","D","D","B","D","D","D","D","D","C","D","D","A","B","D","D","D","D","D","B","D","A","A","D","A","D","D","B","D","D","D","D","D","A","A","A","D","D","D","D","D","D","B","B","B","D","A","D","C","B","B","D","D","B","D","D","A","D","D","A","B","D","D","B","A","D","C","D","D","B","D","B"]
[]
[]
["Normalized Score (ABWRET_E) Based on Wetlands in RWVAU","CD194","GADS1","HANS","MACL","RAUS","RAUS3","MIQUEL01","MIQUEL02","MIQUEL23","MIQUEL36","MLPP10","MIQUEL03","MLPPN","MLPPS","MINHWY","MNSTSE","05CD195","05FAJJColl","05CD89","05FC10","05FC200","05FC13","05FC25","05FC30","HOLM","MITT","MITTEA","MARUS8","CURR",189590,5257,3042,3185,5321,11912,6919,7111,305377,209695,753655,2803,1039,1232,37882,92831,148287,196557,"3042BS",20031,23420,23467,23669,12,52,19555,25411,644242,5062,282535,4507,4647,272004,6926,436864,15082,15434,15186,17152,6174,228332,17902,588706,11568,11491,421060,11488,11698,421953,423143,10763,11808,368499,3410,286841,495717,22720,715354,715420,728347,8245,321809,359454,2882,205184,18237,488834,586891,692585,693500,708592,22645,2939,2966,872,3350,2137,5824,16930,6846,6786,25368,40430,2658,57,4104,14076,841,3014,2944,2953,1828,177552,"05CD90","MITTEA2",6497,1340,23929,25577,662856,444845,505036,13871,421244,636534,421050,20957,309237,368504,206100,1094,10576,7544,34259,99916,166,840,842,107527,25701,"MARUNE",25256,752362,753469,421057,"DALY",148810,23981,738519,752536,2778,11537,191518,186633,21071,421059,6920,"05CD67",15949,212872,208930,842121,735360,"SUMM",7374,3934]
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["Nitrate Removal & Retention (NR)",2.5695746672222217,2.9336912433333335,4.4402865044444448,4.4764931868055555,1.6914084129166671,2.0056871455,4.6400641352380942,3.8568736101190471,3.2168576516666665,4.1323065819047615,3.3348399534523807,1.682834557261905,3.106175454047619,3.6120348909523816,3.2024506065277776,2.3630422644047622,5.1838909549999999,3.9946629041666664,3.2712854415277777,2.4660252172222221,3.428112703333333,3.4804913120833336,4.2353046221428565,3.9380703229166665,3.3967749065476189,2.5460116606944445,3.2001292495833331,2.1455266662500003,2.2448174372619047,2.5084020347619047,2.4099460072619046,2.0432727822619046,3.5199155058333331,3.0405506581944448,2.272652910119048,2.5461526415,1.8697392426190476,2.9490418177777777,3.1531805679166665,2.7294742692857143,4.2148474450000002,4.443907794166666,3.3651167610000003,3.4983680609722216,2.1476501615000001,4.1480610579166672,2.1943686101190476,5.5176250310714288,4.158337349880953,2.2057328345833329,2.5380152748809524,4.5451742553571428,3.3230044772222223,2.9788526708333327,3.3412845866666667,3.538255885555555,5.3932843115000004,1.4229982286904761,4.4674725831944446,3.4311796150000005,2.8097307236904756,1.921963212738095,1.7598951334722224,3.072346536190476,4.7531051345238087,2.6740151854761907,2.3906369845238098,3.5889672084722224,1.7673857737500001,2.2899563541666668,2.3058004759722222,1.6105556189285712,2.783510274027778,3.9887960291666671,2.6310483513888889,1.9030648658333331,1.5813005551190475,2.835170501111111,3.9744762509523808,2.9639155702380955,3.1314536926190479,6.0054455052777778,3.3266159211904762,2.5913834723809521,3.25438605125,2.3690405432142856,4.928631512361112,5.0113241094999994,5.485034905,3.4760307172619047,2.3277053772222223,3.7449050897619047,3.4258679958333333,3.4176963833333334,2.743510734404762,2.9318067580555551,2.0766785791666664,2.7761191609523812,2.6639978639999997,4.7039732804166672,2.4522450722619045,1.8186479683333334,3.4237233447619047,2.8155435877380954,3.4653915135000002,2.379382475595238,3.7754661355555559,3.2857723215476193,3.2176036823809531,3.9759131349999999,4.5276813433333336,4.4074251044047621,3.8510386029761898,3.6367465979166664,1.6374870385000002,6.1058693419444445,2.2050493272619049,3.2734922761904759,3.7895528954761906,3.162459477738095,2.0596887204761902,4.6679404484523799,2.812265587222222,5.1790140937499993,6.065279962,1.7068072394047615,3.4943205172222225,4.7577882139999996,3.5440028000000008,3.848713684861111,1.786012500833333,3.5186528490476192,2.8538865687499997,2.5553426875,6.1206253316666661,3.262662297380952,3.7829664384999999,4.3246962040000003,6.1909894975000004,3.3835472641666668,2.5311135211904761,2.8326296850000006,6.3240268487500009,5.3785637804999995,3.4351695646428571,1.4737404897619046,1.9544873423809526,3.7184399867857145,6.1396755904999996,2.0924093351388886,2.3479355441666669,3.4798483129999997,3.7563922936904763,3.1078048224999999,3.9222594264285711,4.5654533984523811,4.7565445915,3.5789043782142853,2.6402235649999999,5.2268539084523802,2.9500566433333337,4.4178917947619043,3.805430385357143,3.1934931995833331,3.4735435020833334,2.301228287261905,3.1776989183333333,3.3610764479761905,4.0736982045238097,2.8199103517857145,3.2384742958333335,2.571519383,3.3988483797619056,3.8699132373611111,2.2329381287500003]
["Organic Nutrient Export (OE)",0,0,0,0,0,0,0,0,0,0,4.0132451216666665,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,2.4207251272222221,0,0,0,0,0,3.7092822749999996,3.7472036355555556,5.2681940900000015,2.9042841158333332,1.3571323977777778,6.0326157174999997,1.6384050508333332,2.0862607058333333,0,0.24918520249999998,6.8975494794444447,3.0781241855555557,0,5.918954420555556,5.6817260333333328,0,8.2099468688888884,0,0,0,0,0,0,2.9732435149999996,0,0,0,1.1276717255555555,0,0,4.4731992099999998,0,0,2.8854906550000003,4.5085272533333329,3.3880107249999996,0,0,0,0,1.7834034027777779,0,3.5491600744444445,4.9782217150000001,5.9292220233333328,0,0,3.0328005966666667,0,0,0,0,4.1902276000000001,0,0,1.2937295938888891,1.6107559438888888,1.8475200372222222,0,0,0,0,0,0,0,3.1046771450000001,0,5.2614529022222225,6.2660160600000001,0,0,0,5.1758662233333332,6.9423007916666668,0,2.7714183666666665,4.6604687083333332,4.1470658922222219,0,4.0594329591666671,5.0172304661111111,0,3.9765810344444446,0,5.9030376188888889,0,6.0449254966666661,0,7.562596319999999,0,0,3.6394955327777772,3.3195996750000001,0,3.6123201816666661,3.0388066138888892,4.0913026411111115,0,0,6.8134676344444447,0,0,0,0,6.6072282675,0,6.6944140399999998,6.0810897799999992,5.6432340458333341,7.3291948361111103,0,0,0,5.0426246283333329,0,5.8825446766666669,0,4.3742921472222225,7.2063570958333329,6.0745024566666661,0,0,0,0,6.4141381938888884,0,4.3057490127777776,4.0154897033333334,5.3908766833333335,0,5.6021639883333325,0,3.0433799655555553,6.5957743161111102,0,7.3204521733333339,4.3411285758333333,0,5.1441790316666669,3.7337582908333333]
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["Aquatic Invertebrate Habitat (INV)",4.2710411411111115,3.8158456980555555,5.7684989891666669,5.9414650422222213,3.5010318505555555,3.5077966422222229,4.8431862233333334,4.0527127894444446,5.0712264777777785,5.8062731311111104,6.6242591338888888,4.2109126497222222,4.1829425374999998,6.6701624127777768,6.4458978488888885,4.843890516388889,6.5703726747222211,5.6100258447222213,4.1060889136111118,3.5266283322222218,4.6285927405555549,6.6266886619444438,7.5217404983333349,4.7800019291666667,5.0921181433333338,6.3742092372222228,6.5248648283333335,4.8433238999999997,4.1852434824999998,3.5773119950000005,5.8910488611111109,3.8350572936111109,5.4687022536111112,4.018748048611112,4.0503921749999998,4.1019037238888885,4.769371899166666,5.3000989661111095,6.3173415094444438,2.8437885286111113,6.7819561116666662,2.2532809613888891,1.981579985277778,3.5924707424999998,2.685432157777778,5.1295165208333326,4.3283777986111112,6.6919895575000012,5.7136069102777771,4.1261157469444436,3.1945499338888887,4.464252080833333,3.1360721236111111,3.1365482733333332,5.7196585976666654,2.556343875,4.8961295280000003,3.1970654783333337,5.0502861597222228,3.3980186136111108,4.0646709947222224,5.1434725919444437,4.0924298586111103,3.1836528666666668,4.6984797183333331,3.586286860555556,4.4332294855555547,3.4662431188888894,2.9590017386111112,2.6176212122222227,3.6384452197222221,3.3404363177777774,5.9166114813888884,7.953065870555557,5.1257667552777777,5.2471132091666659,5.8169045755555544,4.9837642900000008,7.1074537127777795,4.7040909186111106,4.6085399891666663,5.6839127480555547,3.4390856097222215,6.1145136936111113,4.4052893938888893,5.935652399166667,5.9287252302777782,4.5281483686666668,4.0900464241666672,3.8835406719444436,3.8804821805555556,3.2523951975000003,5.2140986755555554,6.4575481608333343,3.7663835274999995,4.4112850605555547,3.5112654750000001,4.9983060463888886,3.8912952824999998,5.6417056216666666,3.9393971358333335,5.3622977152777764,7.9588238891666663,5.6600181702777785,4.6848922922222229,4.9243794655555559,3.9408506908333329,5.2896725477777782,5.4393630866666678,4.7703143630000007,4.4146408052777781,4.8717333822222226,4.9233261419444441,5.7520284275,4.695867991388889,8.1419086494444457,6.3436164166666673,5.600316895833334,4.9080904002777777,7.3206080225000001,5.4249833663888891,6.5655705488888891,4.9972971883333335,7.93322927861111,6.9809602772222226,3.1510164452777776,2.8684853113888886,4.385587430277778,5.2390874544444443,7.0245505525000009,3.2148278430555557,3.2472481211111108,5.1922240211111106,5.5969938136666659,7.3271411669444442,3.4449813727777774,5.766536857777778,5.1342404373333324,7.1551179713333335,6.4800735666666673,5.906277943888889,4.0889713896666668,5.0498226303333329,3.2226142689999993,3.8037128908333329,6.1259910916666662,7.0518221783333335,4.5314276191666663,4.9278598447222226,5.1056363397222224,4.8291153777777769,6.967911990666666,5.1130057388888881,5.3115235506666654,4.8533996088888891,4.9383942947222224,5.0648716888888892,3.7465096619444442,6.060065274166667,7.8506498936111111,2.9618772550000001,3.104245206111111,4.8123966497222215,4.1025563397222227,4.8965647802777772,4.6143476055555563,3.9329288741666675,4.7343388063888892,5.649885988055555,3.8895325224999993,5.3525748424999993,5.5838250093333333,4.1934217163888894,4.4420199947222221,3.8452681447222226]
["Amphibian Habitat (AM)",4.0932054783333331,5.114861713611111,6.8487647191666667,6.9858827022222227,5.5864651155555558,5.5863667755555557,5.9477120400000008,5.5439722849999997,4.5120917427777778,4.0695250850000004,4.4989948572222218,4.0618772986111109,4.0406460997222222,4.5437925827777788,6.9732585033333327,5.7490437030555555,7.070372674722222,3.9172622991666666,3.932594724166667,5.0191424461111112,4.4556140627777774,6.6266886619444438,7.0217404983333331,2.6427939391666664,4.9922737488888895,5.8856188072222224,6.5362868199999999,4.8547334699999993,5.4556008947222212,3.481099367777778,5.8355492038888892,3.7266338813888882,7.0798365519444451,3.8516449575,5.3337792605555556,6.0456726477777778,5.2123078180555549,5.8297845705555549,6.9558347711111113,2.5719746886111112,6.7952749356666668,2.242570756388889,1.9800810686111112,3.4699576197222219,2.685432157777778,3.3811974197222221,2.5800586975000002,5.1255596530555554,5.684038556388888,4.5534378086111111,2.9836820927777779,4.3177367336111114,4.2510710219444441,3.0090515738888888,7.5437081543333324,4.0606928672222224,4.8961295280000003,3.0422228605555555,4.5189207147222223,3.3304369469444439,3.9432682919444439,4.5637733019444449,2.9323430941666668,3.0046992272222224,4.5748100072222222,3.4168981294444452,3.8850571288888891,4.5475274505555561,2.8888859902777781,3.9292089544444448,3.0513381013888892,3.2413216994444443,3.8009694097222217,5.8347137922222228,3.3730976324999999,3.5031565530555557,4.1009555761111107,3.8757145711111107,6.6310513444444439,6.0473975047222215,4.6878009274999997,6.2225127374999998,3.2847522936111111,6.0590264580555555,4.8372791688888892,7.4453189402777777,6.9781421919444444,6.3892759906666665,2.9233797574999998,4.3337995674999998,2.7156709161111108,2.1243977297222223,3.4766860544444445,6.9677962775000015,3.6018145163888886,3.8501690222222225,5.0945870066666661,6.0922580830555546,6.8734849213888882,7.6897007633333336,3.7985195347222223,5.6082287102777775,7.4910154074999999,5.7565524575000007,4.8685487327777777,4.5534584055555554,2.3406867613888886,5.3196437983333329,3.8310589055555555,4.9599040389999995,4.4859725058333328,4.7868962311111112,3.2233506008333328,4.6436430202777776,3.6724170680555557,8.051861457777779,5.8464417099999997,4.0132614175000008,3.2063486958333338,7.2377009047222218,3.767887363611111,6.4950083694444452,2.8600891983333336,7.889095714722222,8.1798747222222232,2.9902745541666667,2.6595988452777779,6.5006375736111108,5.7738991144444451,6.925389366388889,4.7878391497222221,2.7004546027777776,6.6100318199999997,5.6335171616666671,7.3048604980555556,3.2905863905555552,6.8270241277777775,5.8473166093333333,5.1554459113333344,8.0274137538888883,3.9741762255555564,4.3447316516666667,5.2010933383333331,3.9975376589999998,3.7481573352777775,4.3750719538888889,4.913160781666666,3.4867288808333337,6.3533465569444445,5.0059347986111113,4.6590781999999997,6.9705648326666667,4.9078985611111108,3.3396874866666666,5.7232931072222213,5.8340974247222217,6.6079225655555565,5.2897623452777776,5.7841129297222214,8.5160458280555549,0.96187725499999999,1.3264674283333333,6.1910228413888904,4.5143392847222223,4.6417835441666666,3.0101212161111106,3.867794332499999,6.2520570752777784,3.9708892541666669,4.2268174069444449,5.0927136113888896,3.6126540173333339,4.5955399186111112,2.8441862319444446,4.2780342913888898]
["Waterbird Habitat (WB)",4.1362049183333331,10,7.0962061059722217,7.4525754206944441,10,10,10,10,10,10,10,10,10,10,10,10,6.6647868101388887,3.6571261884722217,10,10,4.22184501,6.8998113108333339,8.3243103324999996,3.2149691441666666,5.8942350929166665,6.0815183809722217,5.4145626974999992,10,5.756954959999999,2.8263124420833337,10,3.4767572733333334,10,10,5.7515000287499998,4.771755906527777,5.7992361237500001,5.600280818611111,4.1988440259722219,1.7673834025000001,5.5634637895000001,2.5331266874999998,1.9697391870833334,2.4214798529166668,10,4.8587597393055555,3.4870084945833328,7.1472458380555546,6.4400239594444439,4.1062026201388884,4.1231956631944442,5.2831073101388881,3.2605825194444442,3.7178821966666664,10,2.9785257837500003,4.6913752745000004,2.4224823187500002,3.9218909297222222,3.6023261983333326,4.2261787212500002,5.2758891222222228,10,3.074958139583333,5.0309286098611103,4.1199274941666664,4.2322908422222225,4.2268660681944441,3.2884962720833331,3.2873970781944446,10,3.5042085866666666,2.7761002726388888,8.0507311522222214,3.4756987312500005,10,4.3171631625,3.9484369498611112,7.1194811005555572,10,10,3.476217325694444,3.3936372862500002,4.8578053173611107,10,6.8519940334722218,6.5475020913888891,5.6766671070000001,3.185819223472222,3.7487131958333331,1.3535442445833334,1.870945322083333,10,6.5937937618055553,10,3.8224552186111111,10,6.4580397976388877,5.1917783027777773,7.9969284101388896,4.5065481687500002,6.7911584436111108,8.5442318377777777,10,2.344068894861111,10,1.9580222224999999,6.7628252558333335,4.9054525161111115,2.8543502549999999,3.3094495170833333,4.5544330787499998,4.9864131316666676,3.9809689691666668,3.6715246504166665,6.2295631805555551,5.7809687019444445,6.4806116640277764,4.7306822033333331,10,10,5.5905458181944443,3.162844534444444,8.1319474976388886,5.7186544880555559,2.3635121533333332,3.6884145508333339,4.324586666388889,5.5857302476388888,6.4449636823611112,4.2122769949999999,3.8841721681944441,6.3285352898611116,5.7320300279999987,8.4146824076388871,4.3789077127777771,5.6610620788888886,2.8754858149999993,4.2128384675000001,10,3.8964025394444439,10,5.9580984000000008,3.9407451890000003,3.5793095247222224,3.8516783245833337,4.4072521888888883,2.2861298029166663,4.0000410744444439,10,4.1873492077777783,6.2408782399999998,4.8704023141666664,3.9555005750000003,7.7651003691666665,7.119105148888889,7.6262209316666674,6.1376945608333324,4.5588761552777779,6.6263066644444448,2.3805452594999998,4.4331094975000003,5.8438033537500003,10,4.8880968140277776,5.3207794229166661,2.9462883808333333,5.4398910725,4.6251188819444442,1.9168568038888889,4.5686157861111116,4.3823090730000001,3.9318499075000002,10,3.0799181234722224]
["Songbird, Raptor, & Mammal Habitat (SBM)",5.399764106388889,5.466813285833334,4.8011929638888891,4.6252543980555556,4.193969097777777,3.9988843002777781,4.5443575730555548,4.3959921790277772,5.3474227329166668,6.3504021395833332,6.6417318615277772,5.15208732375,5.0132626140277781,7.0820918612500003,6.2657694670833317,4.5885868520833331,6.6155772191666662,6.3129977579166674,4.517349543611112,4.3978378744444457,5.419991715138889,6.2594220555555555,7.2447092800000004,5.812361131666667,6.9460154084722223,7.0642249438888891,6.3652385138888885,6.0190488659722217,4.6593623418055561,4.4462511149999999,7.6637869463888899,5.1098150861111105,5.5129751502777777,4.5284009461111108,4.0397722037500001,5.517632743888889,5.9324719830555566,6.2282542476388887,6.763484301388889,3.5678223711111108,7.1365348595370373,4.4739594280555552,4.5883809655555554,4.0612102268055565,5.0509154631481481,6.0594436281944439,5.5687529551388906,5.5968250581944448,6.5542753054166667,5.5917676319444443,5.002707725833333,5.9078967880555542,3.8002796695833334,5.4664270533333337,5.5785340572222228,3.796482842083333,5.4049353174999997,4.1505710177777786,4.7173783813888885,4.5902523630555558,5.7353252147222209,5.1505740188888893,4.0922524833333336,3.93837497125,5.3822387933333342,4.544521026111112,4.6470431801388896,3.545731441388889,3.7453013941666669,5.1862801394444444,3.54272569375,4.1265896869444445,5.4992230147222223,6.6127256931944443,4.7024939055555555,5.8650529213888882,6.2858662377777774,4.7602784758333332,6.9526961274999985,5.9634056437499989,5.7535064913888876,5.4405537781944444,4.6516806066666678,7.157492222916666,5.5874620468518525,5.9549597977777777,4.4009936236111109,3.8727642261111113,4.909259553888889,4.7199758055555563,4.2287470036111108,4.3525413252777776,7.2598629313888896,8.0435897574074087,3.7570091937500001,3.9974777215277779,3.7141067497222218,5.1770054386111122,5.0219162102777783,6.2715963772222221,5.0194271069444438,5.1496418044444434,6.5784818865277774,6.8091834802777775,5.5931268849074076,5.4014194080555553,4.0953240391666661,4.9320724309722221,6.0443845744444449,4.8758917049999999,5.5850398234722212,6.2829128272222228,5.7331204415277783,5.7739096980555562,5.1807957080555553,5.4138807405555553,6.3506343416666668,4.2594550545833334,5.9503713068055566,6.812876874722221,6.6261687691666671,6.8382998620833337,5.6131833002777771,7.8729711827777784,6.444609387685186,4.3263945476388885,4.101795131666667,4.5730693880555568,6.7063369754629631,7.1296927049999992,3.7495641963888886,4.667536823611111,6.6674708094444446,6.9843911670000001,6.671975185,5.4989224734722217,6.0626331549074077,5.1398128600000001,7.266029917,5.9500993870370378,5.9735731488888888,5.0042421313888887,4.8468809999999989,4.9216757899999992,4.1563755949999992,6.5888862783333337,6.8413313234722217,5.2658207330555564,6.4561425675000006,6.2552235365277777,6.4040995408333332,6.4020912640000009,4.7007972741666668,6.1136933976666663,5.1108989241666674,5.4339160284722219,4.555733208055555,5.2210051141666671,7.0072038630555555,6.0998374391666657,3.6855624743333335,3.8365410952777772,4.3013280908333336,5.752731422777777,6.180491175277778,6.1693442194444446,4.3496623086111112,4.7024507062500005,7.2697377886111116,3.6724587733333331,7.2306086849074083,6.5388511569444443,4.5763354481944445,4.5081362894444448,4.8090962283333338]
["Pollinator & Native Plant Habitat (PH)",4.6405176657777787,3.7135779865000003,4.5565913921111107,4.7106499820555561,3.2729990503333335,3.1704653011666668,4.6300720404444444,4.580235762527777,4.996913401583333,6.0282974811944454,6.2072993610833338,5.1553013503611114,5.0456291153611108,6.5414750053055561,6.0135500575370369,4.1229231363055554,5.6974698124444432,5.3213435201296289,4.1373524828703712,3.9780075937222219,4.6421207552870376,5.5541367604444449,6.3933554799629633,4.6186282586666669,5.9582831800277782,6.0227524048148151,5.5414191588888881,4.8539569591851857,4.2983678405277788,5.9132443651111108,6.0750564442962975,4.0470393362407409,4.3983216412592592,4.2585405630555559,3.7464787449166663,4.979004986944445,5.7741547814444436,5.3085034638148141,6.1710056926666654,3.3224444226111109,6.6284667968703701,6.1228995962777777,3.9564848834444444,3.3870721104074075,5.5718084752592585,5.4319498166111115,4.6882037209074072,5.3841750467777771,8.2703853830833332,4.3321744744444439,4.5394330328333332,5.1289089342777769,3.3800332196944445,6.3501108380555547,5.3260201618333323,2.9765979755740739,5.3162690236111123,3.8696795204444445,3.91265264725926,4.2862806070000001,5.1426188060185183,4.6252993174444441,3.9759284149444447,3.8545916004722218,5.3642930480555551,4.7858393702777775,4.3648906471388891,3.772237635222222,4.0475382161666671,4.022088662999999,3.6146671905833334,3.5298799314444445,5.433937687666667,6.607040717916667,5.3112225974444449,5.6273745817777776,6.0302130802777789,4.5188668173333326,6.2941217940370375,4.6771005069166671,4.8696999098888885,6.866382174962963,4.2641718497222225,6.6063750848055545,4.4789562345740741,5.7234131879444448,4.7969089027962957,3.8782041403888883,4.7150771509444445,4.2182088324444438,3.9979955577777764,3.9219951466111107,6.5573287381666665,8.5472264932962965,4.1250729270277775,4.1476447659722222,3.503557787814815,4.4248318884444444,4.2764960000000007,5.3625885810555554,5.0556693002222222,5.4248632355370372,6.6769981123055544,6.4381464339074066,5.4884611614074075,5.3076226198888889,3.7288191161111106,4.345447688851853,6.2219207167222219,4.6197563673888888,5.0376913205833329,5.8438126084444439,5.801038826138889,5.2349845881111099,5.5170237693888904,7.1660234278148138,6.5052826041111098,4.413474755027778,5.8591275199722217,6.5693647889999998,5.833322915351852,7.1148586664722222,5.1251739934259257,6.7514515567222224,7.0671464587407407,3.8658750814722227,4.117258571611111,3.5939944284444447,6.2201830566851859,6.7193420523518519,3.5233856491296294,4.2918500446111114,5.9175809531666665,6.1964542552777777,6.1567443636666663,4.4563022701388881,4.8949118959629629,5.8866162935740727,6.7447083144629625,5.788830331648148,6.0639204674444427,5.2026546651111101,4.7224922857222209,4.6218573827777787,3.5160194550370365,6.4487243043333331,6.5207376250277784,4.650434352907407,6.4843597050555548,5.4138379270833337,7.3638834005555553,5.3632832198888893,6.7721692875185191,5.0121037894444456,4.4080249257222217,4.1176753799814811,4.6452476367777784,4.2965271514074068,6.6642355378333331,5.6818539708333322,2.8834063551666667,4.3449366596111112,3.7383690728888892,4.8624745288333333,5.8229980346666661,5.9291307582777772,3.7310919838518513,4.6319797420277782,6.1200705982222221,3.4828014219999996,6.3439184611296291,6.1414111670555558,4.2512674830555559,4.770387891444444,3.6510905654444441]
["Human Use & Recognition (HU)",2.3544678986249998,5.7238398195000002,2.6571287757499999,2.4477185294999999,3.2926493990000001,3.2844560298749998,6.1696496447500007,5.9936349880000002,5.2302323158750008,4.0644243163749998,4.13197151425,5.2223640912500002,5.9630257283749994,4.7531731893750004,3.7268076806249999,4.0509536496249998,5.8661046350000001,7.2465221624999998,3.0880424980000001,2.8921176153750001,3.3122088600000001,4.5294009136250004,2.1054074648749999,2.3487983617500001,3.6144421106250002,2.6207544847499999,2.694185032,3.0684159583749997,3.68147681075,5.8178332130000001,3.9982200884999997,4.3406450537499994,2.5141265622499995,3.6469901281250001,3.089005615,3.7651420306249999,4.6741075247499992,3.3535998826250002,4.3041325492499993,5.5402060926249996,3.6159751363750003,7.4526073453750001,5.7032895444999996,6.6571565562500004,7.4973077156250003,7.0566636982499995,6.9470041961249995,5.4682595818750004,3.8327719442499997,3.7904654581249995,4.4245206173749994,3.580829783375,3.6729124712500001,6.8373666352499995,7.8438449712500002,3.6506910390000002,2.9376593771250006,5.0968558776249999,5.5621627435000001,4.0339827526249996,5.7500279496250002,4.1679284266250001,4.4782147731249999,3.6950328312500003,5.0629877168749999,5.4226257906250002,4.0048962701249993,3.286394321625,3.7859205787500008,5.1036204125000006,3.9326415028750001,4.0866087936250004,3.3883398732500005,4.0476952930000003,3.4233337067500003,8.1682851186250005,4.3523513084999994,3.122971884,3.444186604375,5.1373805074999996,3.570436123625,3.0423228121249997,4.4720738835000002,7.9431033908749988,3.3969207201249993,4.1659821297499997,3.9834740936250004,3.971724815,3.0247595193749999,4.4759289786250003,4.2499232637499995,4.4228641898749999,4.9497819013750002,3.790533629375,3.768609181875,3.1074692002500006,2.551963539125,2.9915365008750001,2.4141631167500002,3.1343888283750005,5.3104450107499996,4.6554274021249995,4.1798154806249999,3.6536598940000005,3.7699091235000006,3.667753566125,4.3831172568749999,3.8158130135000001,3.7703943200000003,2.8658215218750001,3.6955718415000001,4.0788990333749995,4.9133348535000003,5.2670887539999995,5.8107226081249994,3.6566153648749999,3.7607324482500006,7.9636609561250005,4.8331180255000001,4.3886750226250006,3.910576361375,3.4585891541250002,3.2839664501249999,2.8204436873750005,7.0272788153750003,6.3880732396250011,4.4896569470000003,3.6793827926249998,2.9664968732500001,6.371142050125,4.0390499807499998,4.0801826579999991,2.5501704543749999,3.1949728109999995,5.2381302882499998,3.8867857418749994,5.6584196171250003,3.0237517995000003,2.7618118858750003,2.5782567895000001,4.4865260441250001,6.1783864821250001,5.0537888960000004,6.5810996826250001,2.8683059654999998,4.1391420642499996,4.0560639705000003,3.2210366414999996,1.3721151897500001,2.9358700835000002,3.3970760171249998,3.2375895744999998,3.8080831848749996,3.0542316918750001,3.6320899093749999,3.9263237104999997,2.96622443475,3.8330271836250001,3.8363508028749997,2.6176395558749999,2.9944432435000001,7.2479133778749993,6.458537051875,4.6439716660000006,3.4410795537499999,3.7165341386250006,3.3202065832500005,5.1188557882500003,6.714130037374999,1.9333361681249999,5.5793831357499997,2.83398828775,5.021437824875,6.2233130821249993,5.0158976233749994]
[]
[]
["Function  (ABWRET-ESub ) Normalized:","CD194","GADS1","HANS","MACL","RAUS","RAUS3","MIQUEL01","MIQUEL02","MIQUEL23","MIQUEL36","MLPP10","MIQUEL03","MLPPN","MLPPS","MINHWY","MNSTSE","05CD195","05FAJJColl","05CD89","05FC10","05FC200","05FC13","05FC25","05FC30","HOLM","MITT","MITTEA","MARUS8","CURR",189590,5257,3042,3185,5321,11912,6919,7111,305377,209695,753655,2803,1039,1232,37882,92831,148287,196557,"3042BS",20031,23420,23467,23669,12,52,19555,25411,644242,5062,282535,4507,4647,272004,6926,436864,15082,15434,15186,17152,6174,228332,17902,588706,11568,11491,421060,11488,11698,421953,423143,10763,11808,368499,3410,286841,495717,22720,715354,715420,728347,8245,321809,359454,2882,205184,18237,488834,586891,692585,693500,708592,22645,2939,2966,872,3350,2137,5824,16930,6846,6786,25368,40430,2658,57,4104,14076,841,3014,2944,2953,1828,177552,"05CD90","MITTEA2",6497,1340,23929,25577,662856,444845,505036,13871,421244,636534,421050,20957,309237,368504,206100,1094,10576,7544,34259,99916,166,840,842,107527,25701,"MARUNE",25256,752362,753469,421057,"DALY",148810,23981,738519,752536,2778,11537,191518,186633,21071,421059,6920,"05CD67",15949,212872,208930,842121,735360,"SUMM",7374,3934]
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["Stream Flow Support (SFS)",0.35294628125544286,0.33733279402847244,0.38751269398338695,0.32086581512256201,0.3901774716822235,0.29936678817336793,0.8203015007688621,0.80745397039323474,0.43452825557111452,0.80654690522015382,0.41966060540572381,0.42383035884331216,0.81158833620011261,1,0.51147693566033103,0.37333332085833243,0.76571108221052997,0.47597556620580511,0.24079729819211543,0.24699399128114558,0.81239299712891377,0.50815542304700789,0.55151280629193666,0.44072283695264108,0.46487821046497768,8.2158158844051699E-2,8.4975148494525421E-2,2.8643803221595043E-2,0.26344885278435148,0.58367969914371787,0.28735199934843164,0.30717746931878365,0.25718835687609232,0.13097720838629848,0.34438256210376389,0.51436132482044117,0.58105550664323635,0.63680148261314096,0.44885272542696836,0.83945533270865846,0.47464800536152618,0.93555334423577241,0.50151872353761184,0.32868554007703998,0.21416329413051782,0.51449429879433684,0.40677443570071453,0.71319027661136059,0.39835558882840405,0.18277193224758775,0.14623476972436933,0.16992710724400784,0.31538823756162115,0.29191350444343478,0.82274180658335694,0.31079361665946398,0.21549619270536763,0.29513377668507429,0.73021851709921426,0.26807144600626337,0.66508881177782109,0.3212426965256594,0.66257788277249485,0.51468770453830692,0.77941297665962073,0.42702060467907571,0.49826254654593627,0.25775195747820845,0.47925677192581645,0.63901251926578129,0.36088223063390218,0.3724311568455605,0.63258143987355675,0.45595614124696238,0.43262969420590558,0.39097576672311557,0.45675917390428988,0.51782616713717611,0.39729406495137998,0.45859675179027198,0.62378408434652299,0.33499906799709156,0.37179448071605442,0.51306852200214803,0.4769576706509091,0.41586536273578828,0.33518285133853476,0.33120278876551901,0.31916114914142535,0.57574484451485985,0.38944542196692256,0.57535927746746607,0.92015498207606672,0.8101130256995871,0.35172387610004485,0.32898441906961862,0.27333721527054539,0.40104006414457122,0.26821213277495609,0.22018513700538728,0.13232015614151227,0.29657731237399582,0.15536691307340772,0.32620038836809251,0.28569996100956535,0.36755640293714886,0.52297716506181824,0.3863144136315167,0.15768331804368371,0.13675610408446082,9.6379392061786306E-2,0.32779257078242663,0.60542788216711929,0.50610879252056029,0.47696627497181282,0.19360143649532108,0.31498691795020267,0.16034772791753282,0.58936764537329722,0.14437632978187848,0.5730756800554464,0.1981759406511667,0.28840678002231179,0.13507901658253751,0.37890077811507528,0.49402055198616318,0.21201012537974087,0.33923437955305058,0.31356098342160521,0.2490529395819964,0.44304744390455075,0.44301076871640915,0.76014787695285213,0.54041964884765015,0.36844132914803018,0.45416028503769512,0.4715259212391803,0.3953428278883101,0.3015623240226632,0.31236908538851976,0.53750257889254727,0.44606580529925527,0.22990059088758624,0.30552315271621333,0.60068971999985832,0.39340883312201408,0.40330929816646605,0.35641952762525597,0.54777060163956193,9.252903921420505E-2,0.56982667497113049,9.2374041086494413E-2,0.30728599142973367,0.6507973519577186,0.48949216808084262,0.44903603779718404,0.35989907268636168,0.11657525417411183,0.44125409057095016,0.2897734253499506,0.45969277231015271,0.44741444830767901,0.2958235742330011,0.86159596895954671,0.66009399646762512,0.21916586574900293,0,0.80186663217324949,0.54849877941895497,0.43944935896909898,0.48855201854590441,0.23825826451349627,0.47290891089733855,0.23276523382707937,0.36366144912848219]
["Streamwater Cooling (WC)",0,0,0,0,0,0,0,0,0,0,0.27636591820895523,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0.33333333333333337,0,0,0,0,0,0.36272855328358206,0.51305258955223887,0.40796019900497515,0.32672062885572145,0.49751243781094523,0.51095871999999998,0.30413967900497518,0.49751243781094523,0,0.29850746268656714,0.58706467661691542,0.2388059701492537,0,0.52743745452736324,0.31566075343283584,0,0.33515922069651743,0,0,0,0,0,0,0.93173250965174126,0,0,0,0.2388059701492537,0,0,0.49742279601990053,0,0,0.49751243781094523,0.39800995024875629,0.32835820895522383,0,0,0,0,0.2388059701492537,0,0.35820895522388063,0.52782277990049753,0.35820895522388063,0,0,0.1016538927363184,0,0,0,0,0.44776119402985076,0,0,0.2388059701492537,0.33830845771144274,0.58706467661691542,0,0,0,0,0,0,0,0.12221719681592041,0,0.18856802945273632,0.28855721393034822,0,0,0,0.44776119402985076,0.15920398009950248,0,9.9502487562189046E-2,0.38724853990049751,0.2388059701492537,0,0.19900497512437809,0.42786069651741293,0,0.21749945930348258,0,0.28855721393034822,0,0.10469392179104477,0,0.51741293532338317,0,0,0.2388059701492537,0.45771144278606962,0,0.31840796019900497,0.34825870646766161,0.43054995303482585,0,0,0.46766169154228854,0,0,0,0,0.49751243781094528,0,0.29850746268656714,0.29850746268656714,0.29850746268656714,0.38308457711442784,0,0,0,0.44776119402985076,0,0.37290038835820905,0,0.41017136537313431,0.33744321850746267,0.47761194029850745,0,0,0,0,0.32371060059701495,0,8.5496430845771146E-2,0.47162307582089547,1,0,0.13930348258706465,0,0.58706467661691542,0.52282067920398012,0,0.42369673373134331,0.29850746268656714,0,0.58706467661691542,0.32835820895522388]
["Sediment & Toxicant Retention & Stabilization (SR)",1,1,1,1,1,1,1,1,1,1,0.60669162624615247,1,1,1,1,1,1,1,1,1,1,1,1,1,1,1,1,1,1,0.43175871232518215,1,1,1,1,1,0.77106731517182636,0.35370336187143187,0.59059287435954411,0.64621358966832365,0,0.89194294899893778,0.44789141866904109,0.33459317543885825,1,0.14553417031848501,0.68545690806505843,0.34623053252521785,1,0.63520903518281668,0.71285250079515561,1,0.78664236548816668,1,1,1,1,1,1,0.47849126408923759,1,1,1,7.8150937225369269E-2,1,1,0.33669325656111332,1,1,2.4032120810531181E-2,0.73439338515248109,0.39646420051705422,1,1,1,1,0.15665583209172784,1,0.32455292492853138,0.57701382186887884,0.53796523819844422,1,1,0.36363192269688194,1,1,1,1,0.57050705205502261,1,1,0.16964756687877791,0.2316992438788181,0.34217573259950473,1,1,1,1,1,1,1,0.41180563102917384,1,0.44872834794145239,0.44787630679946749,1,1,1,0.30956426510491408,0.50414849324770783,1,0.3275317979129973,0.43196243658227046,0.37464695588351893,1,0.17505731229586718,0.27845432478518273,1,0.4770271806410501,1,0.45764738785013004,1,0.60902060880006148,1,0.67609241518449059,1,1,0.27442078037995987,0.59975714318971241,1,0.47875444719335086,0.25821288503090645,0.46042047010002141,1,1,0.63184126616047032,1,1,1,1,0.68408376402675941,1,0.73406720156920025,0.51423400655030849,0.7192182554617027,0.7200917097007451,1,1,1,0.68404213942242065,1,0.81502208370353046,1,0.37172201839656971,0.83187562465428144,0.64297918784633479,1,1,1,1,0.58581163873255349,1,0.37856009398675278,0.25347587127619925,0.68867500724656339,1,0.41688874011340266,1,0.2891380384314084,0.72047397793233647,1,0.93419984364798625,0.57824579578811774,1,0.36106219413940382,0.63417377850644918]
["Phosphorus Retention (PR)",1,1,1,1,1,1,1,1,1,1,0.2214703891671197,1,1,1,1,1,1,1,1,1,1,1,1,1,1,1,1,1,1,0.33501630828499857,1,1,1,1,1,0.37676869105233129,0.38490976917865777,0.33143109882516414,0.27902877610783133,0.29828622389692139,0.52612640720670334,0.45215250804118629,0.25729212411816049,1,8.3651509868139032E-2,0.57260068734165293,0.39426981380266701,1,0.31697504199646975,0.23653972813689883,1,0.33734326459423974,1,1,1,1,1,1,0.44722626461936216,1,1,1,0.27489357894326927,1,1,0.23849741280119843,1,1,6.9369010620760729E-2,0.51185864839469553,0.30821923552858232,1,1,1,1,0.20016337900518905,1,0.10910861554390626,0.13946556630018095,0.31283246460269815,1,1,0.30987486384931945,1,1,1,1,0.21019097357937364,1,1,0.19238556600406617,0.23584721350885476,0.46861556956074113,1,1,1,1,1,1,1,0,1,0.33587846849739195,0.46440337296450551,1,1,1,0.32763918407936965,0.51129153938742244,1,0.34235943858595058,0.40944093651002245,0.58646674324093184,1,0.39267099322379484,5.8189643428736559E-2,1,0.16234401947880528,1,0.21841377363181327,1,0.3986512814025211,1,0.45794330249651843,1,1,0.13935757742475341,0.34032239798938835,1,0.28420737410896157,0.22049209476232431,0.26763817292561182,1,1,0.42567888320385805,1,1,1,1,0.48056434990750552,1,0.61321689177709782,9.1380719131482838E-2,0.48377247646292615,0.6465568544111493,1,1,1,0.4969654644908757,1,0.41157745733801715,1,9.393255887436705E-2,0.55131384550656526,0.12440018379926705,1,1,1,1,0.49055526864018523,1,0.57512754888247275,0.11216457525444394,0.63628684544269143,1,0.47178313596774002,1,0.24797731807643347,0.55568325278161712,1,0.57069284136175047,3.3022724986086029E-2,1,0.13749281893966089,0.32141883303821595]
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[]
[]
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[]
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["Value Score (ABWRET_a)",0.72945841596720351,0.94771031730646582,0.79282174224150503,0.80730933162670848,0.91026146798126939,0.91013526139405987,0.95457735035854807,0.95186610803705962,0.94010703256448436,0.92214950536001083,0.5581137636929856,0.9399858343416081,0.95139461820969484,0.93275865080184395,0.90556839890161633,0.91119441205977769,0.84129350586313034,0.83447909885490046,0.90710980493511906,0.90409187538644498,0.7407710532861268,0.81438047421652604,0.83787823562706232,0.74475435988951766,0.80199979817246492,0.79116390115374247,0.77263501114259325,0.90680748746998185,0.74433590380746606,0.30767777774784394,0.92112972832672035,0.74511359494469875,0.89999999999999991,0.91571955652213044,0.73934801471088929,0.39048268745226267,0.33025887667675469,0.35897671108767865,0.41274894728011841,0.34601570058590853,0.52738971760433928,0.45688753635055163,0.17597848679409323,0.70716048200302351,0.45301170894975828,0.56878651234067057,0.40931455385534166,0.83761121256541193,0.44690994841286241,0.39563070812744267,0.74438705349570633,0.6104986845347995,0.67166317828936506,0.80793908274086224,0.98096133118058337,0.66317520848563027,0.71916066820171565,0.72120045289662826,0.46621063114338501,0.72112850683984031,0.79001216318158807,0.74860990966899232,0.41511683222903278,0.69174085973308752,0.76633959117290384,0.23502427910673684,0.72278584251923639,0.70802911290205939,0.15287757714877559,0.43191583328325478,0.46869571319668246,0.70660984823632911,0.74559150837686716,0.85448956400227072,0.73867186600496892,0.45183484221590292,0.77598003486741218,0.14563106337203291,0.37226873619599549,0.48303155457898789,0.90285434868541836,0.78150596018918472,0.23265510057877148,0.87651628969282203,0.91186761160573548,0.83215719494877716,0.81197912836506092,0.32663475622900517,0.71765480884548971,0.71891261198933865,0.13274156165321704,0.1610250343895894,0.58605446921399496,0.86407289225855233,0.91759291600090798,0.70022221280662422,0.89999999999999991,0.77798408638737204,0.78511428971309238,0.83775049414393443,0.29470406024560231,0.8129669411016518,0.46771415326370086,0.52097791966292628,0.74169100568394764,0.90547425212368926,0.69547141394329215,0.28605285166215605,0.4351115862250875,0.71077483037891531,0.2693638543476215,0.32166145179489264,0.40473406285697994,0.77249757189326684,0.31927021352510204,0.44461261336103092,0.79099987941745742,0.42115473862728681,0.78226171768802266,0.51793388903022175,0.92927837640629718,0.49724366501293166,0.74749808851147026,0.44674007544742139,0.88831624974442092,0.71459628324350877,0.17343246576968535,0.34786594204697968,0.78692427648630792,0.37584074455418032,0.22542345566419641,0.2209516327088365,0.77398436292347594,0.80068599247581862,0.51483443581609267,0.75512401430864973,0.81911194677487742,0.74445727594090649,0.80072999768685582,0.54443949754925924,0.77106901732459809,0.62988733778695249,0.38630771953264897,0.54981384462052274,0.49961818858008422,0.79966545979388182,0.81580189058481811,0.72098262843452487,0.45577726996774826,0.90476581666747458,0.5396355914193246,0.80079080526704838,0.29394118012801213,0.61701122950215059,0.43026522829274788,0.79759021651102535,0.82139781882523155,0.7782794694289783,0.81091752660739891,0.51952827159913295,0.66293099950840062,0.44546467351844077,0.30152486634026315,0.69851606725567217,0.77305768654441309,0.41492618417630817,0.70121461314274536,0.38678671664064729,0.54751295176415438,0.68102345591492963,0.69611409895663401,0.34896006034555704,0.71970262809735897,0.44018412953992375,0.37412232592646993]
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["Abundance Factor",0,0,0,-1,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,1,1,1,1,0,0,-1,-1,-1,-1,-1,1,1,1,1,1,0,0,0,0,0,0,0,0,0,0,0,0,-1,-1,-1,0,-1,-1,-1,0,0,0,0,0,0,0,0,0,-1,-1,-1,-1,0,0,0,0,0,0,0,0,-1,-1,-1,-1,-1,-1,0,0,0,0,0,0,0,0,-1,-1,0,0,0,-1,-1,-1,-1,-1,-1,0,0,0,1,-1,1,-1,0,0,0,0,-1,-1,-1,0,0,0,0,0,0,0,-1,0,-1,-1,0,-1,0,0,-1,-1,-1,0,0,-1,-1,-1,0,0,-1,0,-1,-1,0,0,0,-1,0,-1,-1,0,0,0]
["Final Score(A, B, C, D)","C","A","B","C","A","A","A","A","A","A","D","A","A","A","A","A","A","A","A","A","C","B","A","B","B","B","B","A","B","D","A","B","A","A","C","D","D","D","D","D","D","D","D","B","D","D","D","A","D","D","C","D","C","A","A","C","B","C","D","C","B","B","D","D","B","D","C","C","D","D","D","D","B","A","D","D","B","D","D","D","A","B","D","A","A","B","C","D","D","C","D","D","D","A","A","D","A","C","C","B","D","C","D","D","C","A","D","D","D","C","D","D","D","B","D","D","C","D","C","D","A","D","B","D","A","B","D","D","C","D","D","D","B","C","D","C","B","B","B","D","B","D","D","D","D","C","C","C","D","A","D","C","D","D","D","B","B","C","C","D","D","D","D","D","C","D","D","D","D","D","D","D","C","D","D"]

{"sheet":"WS","index":9,"n_rows":133,"n_cols":9,"rows_kept":133,"cut":false,"hidden":false,"merged":[[82,0,85,0],[18,0,23,0],[63,0,66,0],[24,0,28,0],[71,1,75,1],[63,1,66,1],[57,1,62,1],[67,0,70,0],[57,0,62,0],[71,0,75,0],[51,1,56,1],[18,1,23,1],[37,0,43,0],[37,1,43,1],[51,0,56,0],[76,0,81,0],[0,4,0,7],[24,8,28,8],[0,0,0,1],[24,1,28,1],[29,0,36,0],[86,0,90,0],[91,8,95,8],[86,8,90,8],[86,1,90,1],[91,0,95,0],[51,8,56,8],[57,8,62,8],[82,8,85,8],[71,8,75,8],[67,8,70,8],[76,8,81,8],[63,8,66,8],[44,0,50,0],[18,8,23,8],[29,1,36,1],[29,8,36,8],[44,8,50,8],[18,7,23,7],[24,7,28,7],[44,7,50,7],[29,7,36,7],[37,7,43,7],[44,1,50,1],[37,8,43,8],[51,7,56,7],[57,7,60,7],[63,7,66,7],[111,2,111,6],[122,1,123,1],[82,1,85,1],[91,1,95,1],[91,7,95,7],[86,7,90,7],[67,1,70,1],[67,7,70,7],[71,7,75,7],[76,7,81,7],[82,7,85,7],[76,1,81,1]]}
["Water Storage        &                                 Delay",null,"The effectiveness for storing runoff or delaying the downgradient movement of surface water for long or short periods.","WS",null,null,null,null,"The model does not address the likelihood that, based on wetland proximity, valuable infrastructure located downgradient and within flood risk areas may be damaged if water above it is not stored in wetlands or other facilities. The model also does not address the possibility that infrastructure is located within the wetland itself, in which case water storage could threaten that."]
["#","Function Indicators from Estimator","Scoring Notes",null,null,null,"Normalised Score","Indicator Abbreviation     or Formula","Rationale"]
[{"$f":"OF!A2","v":"OF1"},{"$f":"OF!C2","v":"Aquifer Vulnerability Index "},null,null,null,null,{"$f":"IF((AqVul=\"\"),\"\", AqVul)","v":""},"AqVul","Wetlands with greater depth-to-confining layer (represented coarsely by increasing values for Aquifer Vulnerability Index)  potentially allow for faster infiltration. "]
[{"$f":"OF!A5","v":"OF4"},{"$f":"OF!C5","v":"Channel Connection"},"Inverse",null,null,null,{"$f":"IF((ChannConn=\"\"),\"\",1-ChannConn)","v":""},"ChannConn","Wetlands that lack an outlet (never have any outflow) store or dissipate (via evaporation or seepage) nearly all the water they receive (Spence et al. 2011).  This is water that would otherwise contribute to flood damages downgradient of the wetland."]
[{"$f":"OF!A15","v":"OF14"},{"$f":"OF!C15","v":"% of the Wetland that is Fen"},"Inverse",null,null,null,{"$f":"IF((FenPct=\"\"),\"\",1-FenPct)","v":""},"FenPct","Fens are typically groundwater discharge areas. Where groundwater discharges continually, the substrate remains relatively impermeable to the downward infiltration of runoff and thus there may be less capacity to store additional runoff."]
[{"$f":"OF!A19","v":"OF18"},{"$f":"OF!C19","v":"Groundwater Discharge Area or Spring"},"Inverse",null,null,null,{"$f":"IF((GWDspring=\"\"),\"\",1-GWDspring)","v":""},"GWDspring","If a wetland's substrate remains relatively impermeable to the downward infiltration of runoff much of the time, as happens in groundwater discharge wetlands where water is regularly moving upward from subsurface strata, it has less capacity to store additional runoff."]
[{"$f":"OF!A23","v":"OF22"},{"$f":"OF!C23","v":"L/G Index (Residence Time)"},null,null,null,null,{"$f":"IF((LGIndex=\"\"),\"\",LGIndex)","v":""},"LGIndex","Flatter gradients along water flow paths imply greater friction and capacity to slow runoff and surface flow, thus delaying the downgradient movement of water in a watershed."]
[{"$f":"OF!A31","v":"OF30"},{"$f":"OF!C31","v":"% of AA that is Open Water (macro scale)"},null,null,null,null,{"$f":"IF((OWpct=\"\"),\"\",OWpct)","v":""},"OWpct","Wetlands with a greater proportion of open water are more exposed to wind and sun, which increase evaporative water loss."]
[{"$f":"OF!A36","v":"OF35"},{"$f":"OF!C36","v":"Climate Moisture Surplus (P-PET)"},"Inverse",null,null,null,{"$f":"IF((PPET=\"\"),\"\",1-PPET)","v":""},"PPET","Low Net Annual P-PET (Precipitation minus Potential Evapotranspiration) reflects high evaporation in excess of precipitation, and that provides greater space for storing additional runoff.  However, this was modeled at only a broad scale without fully accounting for more localised factors such as wind, wetland shape, and vegetation. "]
[{"$f":"OF!A43","v":"OF42"},{"$f":"OF!C43","v":"Riparian or Floodway Location"},"Inverse",null,null,null,{"$f":"IF((RipFloodpl=\"\"),\"\",1-RipFloodpl)","v":""},"RipFloodpl","Wetlands shown by existing spatial data layers to be located in riparian or floodplain locations are more likely to have at least occasional connections to other surface waters, and thus have greater potential to contribute to downgradient flooding."]
[{"$f":"OF!A48","v":"OF47"},{"$f":"OF!C48","v":"Soil Texture (macroscale)"},"See Table 1.",null,null,null,{"$f":"IF((SoilTex_WS=\"\"),\"\",SoilTex_WS)","v":""},"SoilTex_WS","Loss of water from wetlands via infiltration is more likely to occur when sediments are coarse-textured.  However, this requires that sediments not be continually saturated as commonly occurs where groundwater is discharging."]
[{"$f":"OF!A52","v":"OF51"},{"$f":"OF!C52","v":"Subzero Days"},"Inverse",null,null,null,{"$f":"IF((Sub0Days=\"\"),\"\",1-Sub0Days)","v":""},"Sub0Days","Although ice represents stored water, ice -- when it freezes all the waty to the bottom of a wetland or water body -- also forms a temporarily impervious barrier to infiltration.  Water temporarily stored by infiltration and groundwater recharge would otherwise be mostly unavailable as a contributor to downslope flooding.  During spring runoff, the volume of liquid water (runoff) that moves across the top of ice-covered wetlands (which are slower than uplands to thaw completely) and thus is slowed only slightly may be greater than the amount of fall and winter precipitation stored as ice (and eventually as infiltrate) within the wetland."]
[{"$f":"OF!A63","v":"OF62"},{"$f":"OF!C63","v":"AA Size"},null,null,null,null,{"$f":"IF((WetArea=\"\"),\"\",WetArea)","v":""},"WetArea","Other factors being equal, larger wetlands may be more likely to experience greater water loss per unit area via evaporation and infiltration, due to higher potential for wind and solar exposure."]
[{"$f":"OF!A68","v":"OF67"},{"$f":"OF!C68","v":"Perimeter-Area Ratio"},null,null,null,null,{"$f":"IF((WetPerim2Area=\"\"),\"\",WetPerim2Area)","v":""},"WetPerim2Area","Wetlands with a large Perimeter-Area Ratio have been reported to lose water faster via evapotranspiration (e.g., Millar 1971), thus providing new capacity for storing water more quickly."]
[{"$f":"OF!A69","v":"OF68"},{"$f":"OF!C69","v":"Wetland Vegetated Area"},null,null,null,null,{"$f":"IF((WetVegArea=\"\"),\"\",WetVegArea)","v":""},"WetVegArea","Although vegetation can reduce evaporative water loss by reducing wind and solar exposure, it perhaps more often increases water loss via transpiration.  This indicator describes the area of vegetation, not the proportion of a wetland that is vegetated."]
[{"$f":"OF!A70","v":"OF69"},{"$f":"OF!C70","v":"% of Wetland Classified as Swamp or Forested (macro scale)"},null,null,null,null,{"$f":"IF((WetWooded=\"\"),\"\",WetWooded)","v":""},"WetWooded","Woody vegetation in particular is capable of facilitating higher loss of water via transpiration, because roots penetrate deeper into the water table.  However, woody vegetation also can reduce water loss via shading and wind buffering."]
[{"$f":"OF!A71","v":"OF70"},{"$f":"OF!C71","v":"Wind Energy - Summer"},null,null,null,null,{"$f":"IF((WindSumm=\"\"),\"\",WindSumm)","v":""},"WindSumm","Wind increases the evaporative loss of water from wetlands, creating more space for storage of additional runoff."]
["#","Function Indicators from Onsite Visit","Categorical Choices","Data","Weight","Data  x  Weight","Normalised Score","Indicator Abbreviation or Formula","Rationale & Scoring Notes"]
[{"$f":"F!A39","v":"F8"},{"$f":"F!B39","v":"% Flooded Only Seasonally"},{"$f":"F!C39","v":"The percentage of the AA that is covered by surface water only during the wettest time of year (and for >2 consecutive days during that time) is:"},null,null,null,{"$f":"IF((AllSat+AllSat1>0),\"\",MAX(F20:F24)/MAX(E20:E24))","v":0},"SeasPct1","This directly estimates the relative amount of horizontal space in which precipitation and runoff are being stored, at least temporarily. The ability of wetland water storage to reduce stream peak flows is greatest in summer and fall, where those are the driest times of year (Roulet & Woo 1988, Quinton & Roulet 1998).  In calculations, is excluded automatically (cell goes blank) if wetland never has surface water during an average year."]
[null,null,{"$f":"F!C40","v":"<1%. "},{"$f":"F!D40","v":0},0,{"$f":"D20*E20","v":0}]
[null,null,{"$f":"F!C41","v":"1-25% "},{"$f":"F!D41","v":0},1,{"$f":"D21*E21","v":0}]
[null,null,{"$f":"F!C42","v":"25-50% "},{"$f":"F!D42","v":0},2,{"$f":"D22*E22","v":0}]
[null,null,{"$f":"F!C43","v":"50-95% "},{"$f":"F!D43","v":0},3,{"$f":"D23*E23","v":0}]
[null,null,{"$f":"F!C44","v":">95% "},{"$f":"F!D44","v":0},4,{"$f":"D24*E24","v":0}]
[{"$f":"F!A45","v":"F9"},{"$f":"F!B45","v":"Annual Water Fluctuation Range"},{"$f":"F!C45","v":"The annual fluctuation in surface water level within most of the parts of the AA that contain surface water is:"},null,null,null,{"$f":"IF((AllSat+AllSat1>0=1),\"\",MAX(F26:F29)/MAX(E26:E29))","v":0},"Fluctua1","This directly estimates the relative amount of vertical space in which precipitation and runoff are being stored, at least temporarily (Minke et al. 2010).  In calculations, is excluded automatically (cell goes blank) if wetland never has surface water during an average year."]
[null,null,{"$f":"F!C46","v":"<10 cm change (stable) "},{"$f":"F!D46","v":0},1,{"$f":"D26*E26","v":0}]
[null,null,{"$f":"F!C47","v":"10 cm - 50 cm change"},{"$f":"F!D47","v":0},2,{"$f":"D27*E27","v":0}]
[null,null,{"$f":"F!C49","v":"1-2 m change"},{"$f":"F!D49","v":0},3,{"$f":"D28*E28","v":0}]
[null,null,{"$f":"F!C50","v":">2 m change"},{"$f":"F!D50","v":0},4,{"$f":"D29*E29","v":0}]
[{"$f":"F!A62","v":"F12"},{"$f":"F!B62","v":"% of Water Ponded vs. Flowing "},{"$f":"F!C62","v":"The percentage of the AA's surface water that is ponded (stagnant, or flows so slowly that fine sediment is not held in suspension) during most of the time it is present, and which is either open or shaded by emergent vegetation is:"},null,null,null,{"$f":"IF((AllSat+AllSat1>0=1),\"\",IF((SmallAA=1),\"\",MAX(F31:F37)/MAX(E31:E37)))","v":0},"IsoDry1","Ponding indicates water is in storage rather than being transferred immediately downslope.  Water distributed in small pools is more subject to loss via evapotranspiration before it can exit a wetland.  In calculations, is excluded automatically (cell goes blank) if wetland never has surface water during an average year.  Also is excluded automatically if wetland is <0.01 ha."]
[null,null,{"$f":"F!C63","v":"<1% or none, or occupies <0.01 hectare cumulatively.  Nearly all water is flowing.  Enter \"1\" and SKIP to F21 (Stained Surface Water)."},{"$f":"F!D63","v":0},0,{"$f":"D31*E31","v":0}]
[null,null,{"$f":"F!C64","v":"1-5% of the water, and mainly in small pools.  The rest is flowing."},{"$f":"F!D64","v":0},2,0]
[null,null,{"$f":"F!C65","v":"1-5% of the water, and mainly in a single large pool or pond.  The rest is flowing."},{"$f":"F!D65","v":0},1,0]
[null,null,{"$f":"F!C66","v":"5-30% of the water"},{"$f":"F!D66","v":0},3,0]
[null,null,{"$f":"F!C67","v":"30-70% of the water"},{"$f":"F!D67","v":0},4,0]
[null,null,{"$f":"F!C68","v":"70-95% of the water"},{"$f":"F!D68","v":0},5,0]
[null,null,{"$f":"F!C69","v":">95% of the water.  Little or no visibly flowing water within the AA."},{"$f":"F!D69","v":0},6,0]
[{"$f":"F!A71","v":"F14"},{"$f":"F!B71","v":"% of Ponded Water That Is Open "},{"$f":"F!C71","v":"In ducks-eye aerial view, the percentage of the ponded water that is open (lacking emergent vegetation during most of the growing season, and unhidden by a forest or shrub canopy) is:"},null,null,null,{"$f":"IF((AllSat+AllSat1>0=1),\"\",IF((SmallAA=1),\"\",MAX(F39:F44)/MAX(E39:E44)))","v":0},"OpenPct1","Unvegetated (open) water is susceptible to removal via evaporation due to increased exposure to wind and warming sunlight.  In calculations, is excluded automatically (cell goes blank) if wetland never has surface water during an average year.  Also is excluded automatically if wetland is <0.01 ha."]
[null,null,{"$f":"F!C72","v":"<1% or none, or largest pool occupies <0.01 hectares.  Enter \"1\" and SKIP to F20 (Floating Algae & Duckweed)."},{"$f":"F!D72","v":0},0,0]
[null,null,{"$f":"F!C73","v":"1-5% of the ponded water.  Enter \"1\" and SKIP to F20."},{"$f":"F!D73","v":0},1,0]
[null,null,{"$f":"F!C74","v":"5-30% of the ponded water."},{"$f":"F!D74","v":0},2,0]
[null,null,{"$f":"F!C75","v":"30-70% of the ponded water."},{"$f":"F!D75","v":0},3,0]
[null,null,{"$f":"F!C76","v":"70-99% of the ponded water."},{"$f":"F!D76","v":0},4,0]
[null,null,{"$f":"F!C77","v":"100% of the ponded water. "},{"$f":"F!D77","v":0},5,0]
[{"$f":"F!A84","v":"F16"},{"$f":"F!B84","v":"Predominant Width of Vegetated Zone within Wetland"},{"$f":"F!C84","v":"At the driest time of year (or lowest water level), the average width of vegetated area in the AA that separates adjoining uplands from open water within the AA is:"},null,null,null,{"$f":"IF((AllSat+AllSat1>0=1),\"\",IF((SmallAA=1),\"\",MAX(F46:F51)/MAX(E46:E51)))","v":0},"Vwidth1","Wetland vegetation promotes water loss via evapotranspiration and increased infiltration before that runoff contributes to downgradient flooding.  In calculations, is excluded automatically (cell goes blank) if wetland never has surface water during an average year.  Also is excluded automatically if wetland is <0.01 ha."]
[null,null,{"$f":"F!C85","v":"<1 m"},{"$f":"F!D85","v":0},0,{"$f":"D46*E46","v":0}]
[null,null,{"$f":"F!C86","v":"1 - 9 m"},{"$f":"F!D86","v":0},1,0]
[null,null,{"$f":"F!C87","v":"10 - 29 m"},{"$f":"F!D87","v":0},2,0]
[null,null,{"$f":"F!C88","v":"30 - 49 m"},{"$f":"F!D88","v":0},3,0]
[null,null,{"$f":"F!C89","v":"50 - 100 m"},{"$f":"F!D89","v":0},4,0]
[null,null,{"$f":"F!C90","v":"> 100 m"},{"$f":"F!D90","v":0},5,0]
[{"$f":"F!A109","v":"F25"},{"$f":"F!B109","v":"Through Flow Pattern"},{"$f":"F!C109","v":"During its travel through the AA at the time of peak annual flow, most of the water arriving in channels [select only the ONE encountered by most of the incoming water]:"},null,null,null,{"$f":"IF((AllSat=1),\"\", IF((Inflows=0),\"\",MAX(F53:F57)/MAX(E53:E57)))","v":""},"ThruFlo1","Like a constricted outlet, vegetation and other obstacles create a \"roughness\" within a wetland that can slow the outflow and downstream movement of water. This is much truer if the vegetation intercepts a large proportion of the flow during high-flow periods (i.e., is not merely along an upland edge that never floods), and is tall and stiff enough to provide some resistance. However, the vegetation itself occupies space otherwise available for storing water (this effect is usually negligible). Water also takes longer to move through complex channel networks (e.g., braided or sinuous) which themselves provide additional friction. This indicator is an attempt to represent \"Manning's n\" which is a standard term in stream hydraulic models.  In calculations, is excluded automatically (cell goes blank) if wetland never has surface water during an average year.  Also is excluded automatically if no surface inflow."]
[null,null,{"$f":"F!C110","v":"Does not bump into plant stems as it travels through the AA.  Nearly all the water continues to travel in unvegetated (often incised) channels that have little contact with wetland vegetation, or through a zone of open water such as an instream pond or lake."},{"$f":"F!D110","v":0},0,{"$f":"D53*E53","v":0}]
[null,null,{"$f":"F!C111","v":"bumps into herbaceous vegetation but mostly remains in fairly straight channels."},{"$f":"F!D111","v":0},3,{"$f":"D54*E54","v":0}]
[null,null,{"$f":"F!C112","v":"bumps into herbaceous vegetation and mostly spreads throughout, or is in widely  meandering, multi-branched, or braided channels."},{"$f":"F!D112","v":0},4,{"$f":"D55*E55","v":0}]
[null,null,{"$f":"F!C113","v":"bumps into tree trunks and/or shrub stems but mostly remains in fairly straight channels."},{"$f":"F!D113","v":0},6,{"$f":"D56*E56","v":0}]
[null,null,{"$f":"F!C114","v":"bumps into tree trunks and/or shrub stems and follows a fairly indirect path from entrance to exit (meandering, multi-branched, or braided)"},{"$f":"F!D114","v":0},8,{"$f":"D57*E57","v":0}]
[{"$f":"F!A115","v":"F26"},{"$f":"F!B115","v":"Channel Connection & Outflow Duration"},{"$f":"F!C115","v":"The most persistent surface water connection (outlet channel or pipe, ditch, or overbank water exchange) between the AA and the closest off-site downslope water body is:"},null,null,null,{"$f":"IF((AllSat+AllSat1>0),\"\", MAX(F59:F63)/MAX(E59:E63))","v":0},"OutDura1","Wetlands that store water only temporarily or seasonally have longer periods during the year in which soils are unsaturated and thus able to briefly store or delay additional water from precipitation and runoff. Wetland connectivity is key to estimating wetland water storage: wetlands that lack an outlet (never have any outflow) store or dissipate (via evaporation or seepage) nearly all the water they receive (Spence et al. 2011).  In calculations, is excluded automatically (cell goes blank) if wetland never has surface water during an average year"]
[null,null,{"$f":"F!C116","v":"persistent (>9 months/year, including times when frozen)"},{"$f":"F!D116","v":0},1,{"$f":"D59*E59","v":0}]
[null,null,{"$f":"F!C117","v":"seasonal (14 days to 9 months/year, not necessarily consecutive, including times when frozen)"},{"$f":"F!D117","v":0},2,{"$f":"D60*E60","v":0}]
[null,null,{"$f":"F!C118","v":"temporary (<14 days, not necessarily consecutive -- must be unfrozen)"},{"$f":"F!D118","v":0},3,{"$f":"D61*E61","v":0}]
[null,null,{"$f":"F!C119","v":"none -- but maps show a stream or other water body that is downslope from the AA and within a distance that is less than the AA's length.  If so, mark \"1\" here and SKIP TO F28 (Groundwater). "},{"$f":"F!D119","v":0},9,{"$f":"D62*E62","v":0},null,"NoOutlet1a"]
[null,null,{"$f":"F!C120","v":"no surface water flows out of the wetland except possibly during extreme events (<once per 10 years). Or, water flows only into a wetland, ditch, or lake that lacks an outlet.  If so, mark \"1\" here and SKIP TO F28 (Groundwater). "},{"$f":"F!D120","v":0},10,{"$f":"D63*E63","v":0},null,"NoOutlet1"]
[{"$f":"F!A121","v":"F27"},{"$f":"F!B121","v":"Outflow Confinement"},{"$f":"F!C121","v":"During major runoff events, in the places where surface water exits the AA or connected waters nearby, it:"},null,null,null,{"$f":"IF((OutNone + OutNone1>0),\"\",MAX(F65:F67)/MAX(E65:E67))","v":0},"Constric1","Narrow outlets limit water outflow from a wetland and its downstream or downslope movement, thus increasing storage (Carter et al. 1979). Snowmelt and precipitation tend to be exported downstream more quickly from wetlands that have been drained (Lindsay et al. 2004). The types of outlets described here are ones that typically are more constricted than natural channels, which usually have adjusted over time to local runoff and thus are wider relative to volume of flow received.  In calculations, is excluded automatically (cell goes blank) if no outlet."]
[null,null,{"$f":"F!C122","v":"mostly passes through a pipe, culvert, narrowly breached dike, berm, beaver dam, or other partial obstruction (other than natural topography) that does not appear to drain the wetland artificially during most of the growing season."},{"$f":"F!D122","v":0},2,{"$f":"D65*E65","v":0}]
[null,null,{"$f":"F!C123","v":"leaves through natural exits (channels or diffuse outflow), not mainly through artificial or temporary features"},{"$f":"F!D123","v":0},1,{"$f":"D66*E66","v":0}]
[null,null,{"$f":"F!C124","v":"exported more quickly than usual due to ditches or pipes within the AA (or connected to its outlet or within 10 m of the AA's edge) which drain the wetland artificially, or water is pumped out of the AA."},{"$f":"F!D124","v":0},0,{"$f":"D67*E67","v":0}]
[{"$f":"F!A125","v":"F28"},{"$f":"F!B125","v":"Groundwater: Strength of Evidence"},{"$f":"F!C125","v":"Select first applicable choice. "},null,null,null,{"$f":"IF((D71=1),\"\",MAX(F69:F71)/MAX(E69:E71))","v":0},"Groundw1","Wetlands fed constantly by groundwater are likely to have only limited subsurface storage space for storing additional precipitation (Biswas et al. 2012, Gala et al. 2012).  However, they may remain unfrozen for shorter periods.  In calculations, is excluded automatically (cell goes blank) if no strong evidence of groundwater (last choice)."]
[null,null,{"$f":"F!C126","v":"Groundwater monitoring has demonstrated that groundwater primarily discharges to the wetland for longer periods during the year than periods when the wetland recharges the groundwater.  Or, springs are known to be present within the AA.\n\n\n"},{"$f":"F!D126","v":0},0,{"$f":"D69*E69","v":0}]
[null,null,{"$f":"F!C127","v":"One or more of the following are true: (a) the upper end of the AA is located very close to the base of (but mostly not ON) a natural slope much steeper (usually >15%) than that within the AA and longer than 100 m, OR\n(b) rust deposits (\"iron floc\"), colored precipitates, or dispersible natural oil sheen are prevalent in the AA, OR\n(c) AA water is remarkably clear in contrast to naturally stained waters typical in nearby wetlands, OR\n(d) AA is located at a geologic fault.\n\n"},{"$f":"F!D127","v":0},1,{"$f":"D70*E70","v":0}]
[null,null,{"$f":"F!C128","v":"Neither of above is true, although some groundwater may discharge to or flow through the AA.  Or groundwater influx is unknown."},{"$f":"F!D128","v":0},2,{"$f":"D71*E71","v":0}]
[{"$f":"F!A129","v":"F29"},{"$f":"F!B129","v":"Internal Gradient"},{"$f":"F!C129","v":"The gradient along most of the flow path within the AA is:"},null,null,null,{"$f":"MAX(F73:F76)/MAX(E73:E76)","v":0},"Gradient1","Unless impounded, steeply sloping wetlands retain less surface runoff and precipitation."]
[null,null,{"$f":"F!C130","v":"<2%, or, no slope is ever apparent (i.e., flat). Or, the wetland is in a depression or pond with no inlet and no outlet."},{"$f":"F!D130","v":0},4,{"$f":"D73*E73","v":0}]
[null,null,{"$f":"F!C131","v":"2-5%"},{"$f":"F!D131","v":0},3,{"$f":"D74*E74","v":0}]
[null,null,{"$f":"F!C132","v":"6-10%"},{"$f":"F!D132","v":0},2,{"$f":"D75*E75","v":0}]
[null,null,{"$f":"F!C133","v":">10%"},{"$f":"F!D133","v":0},0,{"$f":"D76*E76","v":0}]
[{"$f":"F!A134","v":"F30"},{"$f":"F!B134","v":"Total Woody Cover -% of the Vegetated AA"},{"$f":"F!C134","v":"Within the entire vegetated part of the AA, the percentage occupied by trees or shrubs taller than 1 m is:"},null,null,null,{"$f":"MAX(F78:F82)/MAX(E78:E82)","v":0},"AllWoody1","Woody vegetation in particular is capable of facilitating higher loss of water via transpiration, because roots penetrate deeper into the water table.  However, woody vegetation also can reduce water loss via shading and wind buffering."]
[null,null,{"$f":"F!C135","v":"<5% of the vegetated AA, or there is no woody vegetation in the AA.  SKIP to F38 (N Fixers)"},{"$f":"F!D135","v":0},0,{"$f":"D78*E78","v":0}]
[null,null,{"$f":"F!C136","v":"5-25%.  "},{"$f":"F!D136","v":0},1,{"$f":"D79*E79","v":0}]
[null,null,{"$f":"F!C137","v":"25-50%"},{"$f":"F!D137","v":0},2,{"$f":"D80*E80","v":0}]
[null,null,{"$f":"F!C138","v":"50-75%"},{"$f":"F!D138","v":0},3,{"$f":"D81*E81","v":0}]
[null,null,{"$f":"F!C139","v":">75%"},{"$f":"F!D139","v":0},4,{"$f":"D82*E82","v":0}]
[{"$f":"F!A200","v":"F42"},{"$f":"F!B200","v":"Ground Irregularity"},{"$f":"F!C200","v":"Consider the parts of the AA that lack surface water at some time of the year.  Excluding slash from logging, the number of small pits, raised mounds, hummocks, boulders, upturned trees, animal burrows, gullies, natural levees, wide soil cracks, and microdepressions is:"},null,null,null,{"$f":"MAX(F84:F86)/MAX(E84:E86)","v":0},"Girreg1","Large variation in elevations within a wetland suggest greater potential for trapping and retaining snow and other precipitation, sufficiently long to allow infiltration or evaporation.  Rough surfaces also allow for more runoff interception and infiltration."]
[null,null,{"$f":"F!C201","v":"Few or none (minimal microtopography; <1% of that area) "},{"$f":"F!D201","v":0},0,{"$f":"D84*E84","v":0}]
[null,null,{"$f":"F!C202","v":"Intermediate"},{"$f":"F!D202","v":0},1,{"$f":"D85*E85","v":0}]
[null,null,{"$f":"F!C203","v":"Several (extensive micro-topography)"},{"$f":"F!D203","v":0},2,{"$f":"D86*E86","v":0}]
[{"$f":"F!A208","v":"F44"},{"$f":"F!B208","v":"Soil Texture"},{"$f":"F!C208","v":"In parts of the AA that lack persistent water, the texture of soil in the uppermost layer is mostly:  [To determine this, use a trowel to check in at least 3 widely spaced locations, and use the soil texture key in Appendix A of the Manual]"},null,null,null,{"$f":"MAX(F88:F91)/MAX(E88:E91)","v":0},"SoilTex1","Considerable amounts of water can be stored below the land surface in peat and coarse-textured substrates. However, very little new runoff can be stored if the substrates are already saturated. Peat tends to be saturated much of the time, and groundwater discharge dominates many wetlands with coarse-textured substrate, keeping those saturated much of the time and thus limiting the capacity to store additional water. At any rate, the uppermost soil layer is not necessarily a strong indicator of underlying soil structure which exerts greater influence on water storage, but is impossible to assess rapidly."]
[null,null,{"$f":"F!C209","v":"Loamy: includes loam, sandy loam"},{"$f":"F!D209","v":0},1,{"$f":"D88*E88","v":0}]
[null,null,{"$f":"F!C210","v":"Fines: includes silt, glacial flour, clay, clay loam, silty clay, silty clay loam, sandy clay, sandy clay loam."},{"$f":"F!D210","v":0},0,{"$f":"D89*E89","v":0}]
[null,null,{"$f":"F!C211","v":"Organic"},{"$f":"F!D211","v":0},3,{"$f":"D90*E90","v":0}]
[null,null,{"$f":"F!C212","v":"Coarse: includes sand, loamy sand, gravel, cobble, stones, boulders, fluvents, fluvaquents, riverwash."},{"$f":"F!D212","v":0},2,{"$f":"D91*E91","v":0}]
[{"$f":"F!A323","v":"F68"},{"$f":"F!B323","v":"Wetland as a % of Its Contributing Area (Catchment)"},{"$f":"F!C323","v":"View the approximate boundaries of the wetland's catchment (CA) as shown in the map AESRD provides in response to your data request.  Then adjust those boundaries if necessary based on your field observations of the surrounding terrain, and/or by using procedures described in the ABWRET Manual. Relative to the extent of this catchment (but excluding the area of the AA), this AA and any bordering waters together comprise (select ONE):"},null,null,null,{"$f":"MAX(F93:F96)/MAX(E93:E96)","v":0},"WetPctCA","Wetlands that comprise a large portion of their contributing area have a greater potential to control the runoff arriving from that limited area (McAllister et al. 2000, Ehsanzadeh et al. 2012). "]
[null,null,{"$f":"F!C324","v":"<1% of their catchment"},{"$f":"F!D324","v":0},1,{"$f":"D93*E93","v":0}]
[null,null,{"$f":"F!C325","v":"1 to 10% of their catchment"},{"$f":"F!D325","v":0},2,0]
[null,null,{"$f":"F!C326","v":"10 to 100%  of their catchment"},{"$f":"F!D326","v":0},3,0]
[null,null,{"$f":"F!C327","v":"Larger than the area of their catchment (wetland has essentially no catchment, e.g., isolated by dikes with no input channels, or is a raised bog). "},{"$f":"F!D327","v":0},4,0," "]
[null,null,null,null,null,null,null," "]
[null,null,"Infiltration Capacity of Wetland [INFILT]"]
[null,"Wetlands <10 hectares:","[AVERAGE(1-GWDspring, 1-FenPct, Groundw1) + AVERAGE(1-Sub0Days, AVERAGE(SoilTex1, AquifVul)) + AVERAGE(1-PPET, WindSumm, WetPerim2Area, OpenPct1) + AVERAGE(WetVegArea, AllWoody1)] / 4",null,null,null,{"$f":"IF((GT10HA=1),G100, IFERROR((AVERAGE(1-GWDspring, 1-FenPct, Groundw1) + AVERAGE(1-Sub0Days, AVERAGE(SoilTex1, AqVul)) + AVERAGE(1-PPET, WindSumm, WetPerim2Area, OpenPct1) + AVERAGE(WetVegArea, AllWoody1)) / 4,\"\"))","v":0.41666666666666663},null,"In wetlands >10 ha, GIS indicators in bold are substituted for field indicators denoted with red font in the cell above, because in large wetlands tnose GIS-derived indicators are assumed to yield more accurate estimates of the similar field indicator."]
[null,"Wetlands >10 hectares:","substituted SoilTex, OWpct, WetWooded",null,null,null,{"$f":"IFERROR((AVERAGE(1-GWDspring, 1-FenPct, Groundw1) + AVERAGE(1-Sub0Days, AVERAGE(SoilTex_WS, AqVul)) + AVERAGE(1-PPET, WindSumm, WetPerim2Area, OWpct) + AVERAGE(WetVegArea, WetWooded)) / 4,\"\")","v":""}]
[]
[null,null,"Flow Resistance & Delay [RESIST]"]
[null,"Wetlands <10 hectares:","AVERAGE(ThruFlo1, Gradient1, Girreg1, Constric1, IsoDry1, vwidth1) ",null,null,null,{"$f":"IF((GT10HA=1),G104, IFERROR(AVERAGE(ThruFlo1, Gradient1, Girreg1, Constric1, IsoDry1, Vwidth1),\"\"))","v":0}]
[null,"Wetlands >10 hectares:","Included LGIndex in above average",null,null,null,{"$f":"IFERROR(AVERAGE(ThruFlo1, Gradient1, Girreg1, Constric1, IsoDry1, Vwidth1, LGIndex),\"\")","v":0}]
[]
[null,null,"Surface Storage Capacity [STORE]"]
[null,null,"AVERAGE(WetArea, AVERAGE(WetPctCA1, ElevPctileHUC8), Fluctua1, SeasPct1)",null,null,null,{"$f":"IFERROR(AVERAGE(WetArea, WetPctCA1, Fluctua1, SeasPct1, ElevPctileHUC8),\"\")","v":0}]
[]
[null,null,"ABWRET-A FUNCTION MODEL"]
[null,null,"Water Storage & Delay"]
[null,null,"IF((OutNone + OutNone1>0),10, ELSE: 10*AVERAGE(INFILT, STORE, RESIST)",null,null,null,{"$f":"IF((NoOutlet1 + NoOutlet1a>0),10, 10*AVERAGE(INFILT1a, STORE1a, RESIST1a))","v":1.3888888888888886}]
[]
[null,null,"ABWRET-E:",null,null,null,null,null,"Literature Cited"]
[null,1,"IF(ChannConn + RipFloodPl = 0), then =10",{"$f":"IF((ChannConn+RipFloodpl=0), 10, \"\")","v":10},null,null,null,null,"Arnold, C. L. and C. J. Gibbons. 1996. Impervious surface coverage: The emergence of a key environmental indicator. Journal of the American Planning Association 62:243-258."]
[null,2,"ELSE calculate these averages:",null,null,null,null,null,"Biswas, A., H. W. Chau, A. K. Bedard-Haughn, and B. C. Si. 2012. Factors controlling soil water storage in the hummocky landscape of the Prairie Pothole Region of North America. Canadian Journal of Soil Science 92:649-663."]
[null,null,"a. AVERAGE(1-GWDspring, 1-FenPct) ",{"$f":"IFERROR(AVERAGE(1-GWDspring, 1-FenPct),\"\")","v":1},null,null,null,null,"Booth, D. B. and C. R. Jackson. 1997. Urbanization of aquatic systems: Degradation thresholds, stormwater detection, and the limits of mitigation. JAWRA Journal of the American Water Resources Association 33:1077-1090."]
[null,null,"b. AVERAGE [1-Sub0Days, AVERAGE(SoilTex, AqVul) ]",{"$f":"IFERROR(AVERAGE(1-Sub0Days, AVERAGE(SoilTex_WS, AqVul)),\"\")","v":""},null,null,null,null,"Carter, V., M. S. Bedinger, R. P. Novitski, and W. Wilen. 1979. Water resources and wetlands. Pages 344–376 in P. E. Greeson, J. R. Clark, and J. E. Clark, editors. Wetland Functions and Values: The State of Our Understanding. American Water Resources Association, Minneapolis, MN."]
[null,null,"c. AVERAGE(1-PPET, WindSumm, WetPerim2Area, OWpct, WetArea) ",{"$f":"IFERROR(AVERAGE(1-PPET, WindSumm, WetPerim2Area, OWpct, WetArea),\"\")","v":1},null,null,null,null,"Detenbeck, N., C. Elonen, D. Taylor, A. Cotter, F. Puglisi, and W. Sanville. 2002. Effects of agricultural activities and best management practices on water quality of seasonal prairie pothole wetlands. Wetlands Ecology and Management 10:335-354."]
[null,null,"d. AVERAGE(WetVegArea, WetWooded)",{"$f":"IFERROR(AVERAGE(WetVegArea, WetWooded),\"\")","v":""},null,null,null,null,"Gala, T. S., R. J. Trueman, and S. Carlyle. 2012. Soil hydrodynamics and controls in prairie potholes of central Canada. Area 44:305-316."]
[null,null,"e. AVERAGE(WetPctHUC8, ElevPctileHUC8)",{"$f":"IFERROR(AVERAGE(WetPctHUC8, ElevPctileHUC8),\"\")","v":""},null,null,null,null,"Hirsch, R. M., J. F. Walker, J. C. Day, and R. Kollio. 1990. The influence of man on hydrologic systems. Pages 329–359 in M. G. Wolaman and H. C. Riggs, editors. Surface Water Hydrology. Geological Society of America, Boulder, CO. "]
[null,null,"f. L/G Index",{"$f":"IF((LGIndex=\"\"),\"\")","v":""},null,null,null,null,"Laenen, A. 1980. Storm Runoff as Related to Urbanization in the Portland, Oregon-Vancouver, Washington Area: U.S. Geological Survey Water Resources Investigations 80-689. Geological Survey, Portland, OR."]
[null,3,"MAX [ #1, 10*AVERAGE(WatProb, a, b, c, d, e, f)]",{"$f":"MAX(D114, 10*AVERAGE(WatProb, D116:D121))","v":10},null,null,null,null,"Leopold, L. B. 1968. Hydrology for Urban Land Planning—A Guidebook on the Hydrologic Effects of Urban Land Use. United States Department of the Interior, U.S. Geological Survey, Circular 554, Washington, DC."]
[null,null,null,null,null,null,null,null,"Lindsay, J. B., I. F. Creed, and F. D. Beall. 2004. Drainage basin morphometrics for depressional landscapes. Water Resources Research 40."]
[null,null,"ABWRET-E with substitutions:",null,null,null,null,null,"Millar, J. B. 1971. Shoreline-area ratio as a factor in rate of water loss from small sloughs. Journal of Hydrology 14:259-284."]
[null,1,"IF(OutNone+OutNone1>0), then =10",{"$f":"IF((OutNone+OutNone1>0), 10, \"\")","v":""},null,null,null,null,"Minke, A. G., C. J. Westbrook, and G. van der Kamp. 2010. Simplified volume-area-depth method for estimating water storage of prairie potholes. Wetlands 30:541-551."]
[null,2,"ELSE calculate these averages:",null,null,null,null,null,"Quinton, W. L. and N. T. Roulet. 1998. Spring and summer runoff hydrology of a subarctic patterned wetland. Arctic and Alpine Research 30:285-294."]
[null,null,"a. AVERAGE(1-GWDspring, 1-FenPct) ",{"$f":"IFERROR(AVERAGE(1-GWDspring, 1-FenPct),\"\")","v":1},null,null,null,null,"Roulet, N. T. and M. K. Woo. 1988. Run-off generation in a low arctic drainage-basin. Journal of Hydrology 101:213-226."]
[null,null,"b. AVERAGE [1-Sub0Days, AVERAGE(SoilTex1, AqVul) ]",{"$f":"IFERROR(AVERAGE(1-Sub0Days, AVERAGE(SoilTex1, AqVul)),\"\")","v":0.5},null,null,null,null,"Spence, C., X. J. Guan, and R. Phillips. 2011. The hydrological functions of a boreal wetland. Wetlands 31:75-85."]
[null,null,"c. AVERAGE(1-PPET, WindSumm, WetPerim2Area, OpenPct1, WetArea) ",{"$f":"IFERROR(AVERAGE(1-PPET, WindSumm, WetPerim2Area, OpenPct1, WetArea),\"\")","v":0.5},null,null,null,null,"Waite, T. A. and L. G. Campbell. 2006. Controlling the false discovery rate and increasing statistical power in ecological studies. Ecoscience 13:439-442."]
[null,null,"d. AVERAGE(WetVegArea, AllWoody1)",{"$f":"IFERROR(AVERAGE(WetVegArea, AllWoody1),\"\")","v":0}]
[null,null,"e. AVERAGE(WetPctHUC8, ElevPctileHUC8)",{"$f":"IFERROR(AVERAGE(WetPctHUC8, ElevPctileHUC8),\"\")","v":""}]
[null,null,"f. L/G Index",{"$f":"IF((LGIndex=\"\"),\"\")","v":""}]
[null,3,"10*MAX[ #1, AVERAGE(SeasPct1, a, b, c, d, e, f)]",{"$f":"MAX(D125, 10*AVERAGE(SeasPct1, D127:D132))","v":4}]

{"sheet":"SFS","index":10,"n_rows":101,"n_cols":9,"rows_kept":101,"cut":false,"hidden":false,"merged":[[45,8,49,8],[18,1,22,1],[39,1,44,1],[45,1,49,1],[18,8,22,8],[29,8,34,8],[35,8,38,8],[23,1,28,1],[23,8,28,8],[39,8,44,8],[45,7,49,7],[39,7,44,7],[35,7,38,7],[29,7,34,7],[0,4,0,7],[0,0,0,1],[23,0,28,0],[23,7,28,7],[18,7,22,7],[62,1,62,3],[29,1,34,1],[35,0,38,0],[29,0,34,0],[35,1,38,1],[45,0,49,0],[39,0,44,0]]}
["Stream                       Flow                         Support",null,"The effectiveness for contributing water to streams during the driest part of a growing season.","SFS",null,null,null,null,"This function is likely to be most beneficial to aquatic life and human use of stream water where there are stream segments that periodically dry up due to local climate (low P-PET), headwater location, artificial diversions, or other factors.  However, the model does not address such ecological or economic needs for supporting stream flow at a particular location.  "]
["#","Function Indicators from Estimator","Scoring Notes",null,null,null,"Normalised Score","Indicator Abbreviation      or Formula","Rationale"]
[{"$f":"OF!A5","v":"OF4"},{"$f":"OF!C5","v":"Channel Connection"},null,null,null,null,{"$f":"IF((ChannConn=\"\"),\"\",ChannConn)","v":""},"ChannConn","Wetlands that have no outflow are likely to have only minimal effect on volume of flow reaching downstream water bodies."]
[{"$f":"OF!A12","v":"OF11"},{"$f":"OF!C12","v":"Elevation Percentile Within HUC8 "},null,null,null,null,{"$f":"IF((ElevPctileHUC8=\"\"),\"\",ElevPctileHUC8)","v":""},"ElevPctileHUC8","Headwater wetlands are more likely than lowland wetlands to be in a position to measurably influence water volume and persistence in downgradient channels."]
[{"$f":"OF!A15","v":"OF14"},{"$f":"OF!C15","v":"% of the Wetland that is Fen"},null,null,null,null,{"$f":"IF((FenPct=\"\"),\"\",FenPct)","v":""},"FenPct","Fens are typically groundwater discharge areas, and such discharge is more seasonally stable and thus more likely to contribute water late in the season when flow in receiving streams otherwise can be low."]
[{"$f":"OF!A19","v":"OF18"},{"$f":"OF!C19","v":"Groundwater Discharge Area or Spring"},null,null,null,null,{"$f":"IF((GWDspring=\"\"),\"\",GWDspring)","v":""},"GWDspring","See above."]
[{"$f":"OF!A31","v":"OF30"},{"$f":"OF!C31","v":"% of AA that is Open Water (macro scale)"},"Inverse",null,null,null,{"$f":"IF((OWpct=\"\"),\"\",1-OWpct)","v":""},"OWpct","Open water experiences more water loss from evaporation due to wind and solar heating, and that can mean less water available to subsidize downgradient streams."]
[{"$f":"OF!A36","v":"OF35"},{"$f":"OF!C36","v":"Climate Moisture Surplus (P-PET)"},null,null,null,null,{"$f":"IF((PPET=\"\"),\"\",PPET)","v":""},"PPET","Wetlands in regions with intrinsically large precipitation deficits may be less capable of subsidizing flow in downgradient streams."]
[{"$f":"OF!A43","v":"OF42"},{"$f":"OF!C43","v":"Riparian or Floodway Location"},null,null,null,null,{"$f":"IF((RipFloodpl=\"\"),\"\",RipFloodpl)","v":""},"RipFloodpl","Wetlands that are not in riparian or floodplain locations are likely to have only minimal effect on volume of flow reaching downstream water bodies."]
[{"$f":"OF!A50","v":"OF49"},{"$f":"OF!C50","v":"Soil Texture (macroscale)"},"See Table 3 worksheet.",null,null,null,{"$f":"IF((SoilTex_NROE=\"\"),\"\",SoilTex_NROE)","v":""},"SoilTex_NROE"]
[{"$f":"OF!A52","v":"OF51"},{"$f":"OF!C52","v":"Subzero Days"},"Inverse",null,null,null,{"$f":"IF((Sub0Days=\"\"),\"\",Sub0Days)","v":""},"Sub0Days","Wetlands that remain frozen for longer in the spring may have more potential to subsidize flow in receiving streams as wetland ice gradually melts."]
[{"$f":"OF!A61","v":"OF60"},{"$f":"OF!C61","v":"Water Permanence Probability"},null,null,null,null,{"$f":"IF((WatProb=\"\"),\"\",WatProb)","v":""},"WatProb","More permanent surface water in a wetland implies more potential for some of that water to subsidize flow in receiving streams."]
[{"$f":"OF!A67","v":"OF66"},{"$f":"OF!C67","v":"Wetland as a % of Its HUC8"},null,null,null,null,{"$f":"IF((WetPctHUC8=\"\"),\"\",WetPctHUC8)","v":""},"WetPctHUC8","Wetlands that comprise a larger proportion of their watershed are more likely to have measurable effect on downgradient waters."]
[{"$f":"OF!A68","v":"OF67"},{"$f":"OF!C68","v":"Perimeter-Area Ratio"},"Inverse",null,null,null,{"$f":"IF((WetPerim2Area=\"\"),\"\",1-WetPerim2Area)","v":""},"WetPerim2Area","Wetlands with large perimeter-to-area ratio tend to lose more water to evapotranspiration (Millar 1971) and so are less able to subsidize downstream flows."]
[{"$f":"OF!A69","v":"OF68"},{"$f":"OF!C69","v":"Wetland Vegetated Area"},"Inverse",null,null,null,{"$f":"IF((WetVegArea=\"\"),\"\",1-WetVegArea)","v":""},"WetVegArea","Evapotranspiration from vegetation can represent a significant loss of water that otherwise might subsidize downstream flows."]
[{"$f":"OF!A70","v":"OF69"},{"$f":"OF!C70","v":"% of Wetland Classified as Swamp or Forested (macro scale)"},"Inverse",null,null,null,{"$f":"IF((WetWooded=\"\"),\"\",1-WetWooded)","v":""},"WetWooded","Late in the growing season, woody vegetation transpires significant amounts of water, thus making that water unavailable for subsidizing stream flow.  However, woody plants can also intercept drifting snow during the winter, and  significant amounts of precipitation early during the growing season, for later use in subsidizing stream flow (Kort et al. 2012). "]
[{"$f":"OF!A71","v":"OF70"},{"$f":"OF!C71","v":"Wind Energy - Summer"},"Inverse",null,null,null,{"$f":"IF((WindSumm=\"\"),\"\",1-WindSumm)","v":""},"WindSumm","Wetlands in regions with persistent summer winds experience more evaporative loss of their water and thus may be less capable of subsidizing flow in downgradient streams."]
["#","Function Indicators from Onsite Visit","Categorical Choices","Data","Weight","Data  x  Weight","Normalised Score","Indicator Abbreviation or Formula","Rationale & Scoring Notes"]
[{"$f":"F!A6","v":"F1"},{"$f":"F!B6","v":"Wetland Type - Predominant"},{"$f":"F!C6","v":"Most of the vegetated part of the AA (wetland Assessment Area) is a (select ONE):"},null,null,null,{"$f":"MAX(F20:F23)/MAX(E20:E23)","v":0},"Wettype2","Fens are typically groundwater discharge areas, and such discharge is more seasonally stable and thus more likely to contribute water late in the season when streamflow otherwise can be low. Some bogs with outlets discharge capillary water and thus potentially influence low flows (Siegal 1988). Water tables in riparian wetlands typically fluctuate with river levels, and so are not likely to contribute much water during low flow conditions. Wooded swamps lose water via transpiration, but retain it by shading the ground and reducing evaporation."]
[{"$f":"F!A7","v":"F1.1"},null,{"$f":"F!C7","v":"Wooded Swamp"},{"$f":"F!D7","v":0},2,{"$f":"D20*E20","v":0}]
[{"$f":"F!A8","v":"F1.2"},null,{"$f":"F!C8","v":"Bog"},{"$f":"F!D8","v":0},3,{"$f":"D21*E21","v":0}]
[{"$f":"F!A9","v":"F1.3"},null,{"$f":"F!C9","v":"Fen"},{"$f":"F!D9","v":0},4,{"$f":"D22*E22","v":0}]
[{"$f":"F!A10","v":"F1.4"},null,{"$f":"F!C10","v":"Marsh or Shallow Open Water"},{"$f":"F!D10","v":0},1,{"$f":"D23*E23","v":0}]
[{"$f":"F!A52","v":"F10"},{"$f":"F!B52","v":"Predominant Depth Class"},{"$f":"F!C52","v":"During most of the time when water is present, its depth in most of the area is: [Note: This is not asking for the maximum depth.]"},null,null,null,{"$f":"IF((AllSat+AllSat1>0),\"\", IF((SmallAA=1),\"\", MAX(F25:F29)/MAX(E25:E29)))","v":0},"Depth2_","Deeper water implies greater water volume to potentially feed downslope streams. In calculations, is excluded automatically (cell goes blank) if wetland never has surface water during an average year.  Also is excluded automatically if wetland is <0.01 ha."]
[null,null,{"$f":"F!C53","v":"<10 cm deep (but >0)"},{"$f":"F!D53","v":0},0,{"$f":"D25*E25","v":0}]
[null,null,{"$f":"F!C54","v":"10 - 50 cm deep"},{"$f":"F!D54","v":0},1,{"$f":"D26*E26","v":0}]
[null,null,{"$f":"F!C55","v":"0.5 - 1 m deep"},{"$f":"F!D55","v":0},2,{"$f":"D27*E27","v":0}]
[null,null,{"$f":"F!C56","v":"1 - 2 m deep"},{"$f":"F!D56","v":0},3,{"$f":"D28*E28","v":0}]
[null,null,{"$f":"F!C57","v":">2 m deep.  True for many fringe wetlands."},{"$f":"F!D57","v":0},4,{"$f":"D29*E29","v":0}]
[{"$f":"F!A115","v":"F26"},{"$f":"F!B115","v":"Channel Connection & Outflow Duration"},{"$f":"F!C115","v":"The most persistent surface water connection (outlet channel or pipe, ditch, or overbank water exchange) between the AA and the closest off-site downslope water body is:"},null,null,null,{"$f":"MAX(F31:F35)/MAX(E31:E35)","v":0},"OutDur2_","This is the primary indicator of a wetland's potential for supporting summer flow in connected downslope streams. "]
[null,null,{"$f":"F!C116","v":"persistent (>9 months/year, including times when frozen)"},{"$f":"F!D116","v":0},6,{"$f":"D31*E31","v":0}]
[null,null,{"$f":"F!C117","v":"seasonal (14 days to 9 months/year, not necessarily consecutive, including times when frozen)"},{"$f":"F!D117","v":0},3,{"$f":"D32*E32","v":0}]
[null,null,{"$f":"F!C118","v":"temporary (<14 days, not necessarily consecutive -- must be unfrozen)"},{"$f":"F!D118","v":0},2,{"$f":"D33*E33","v":0}]
[null,null,{"$f":"F!C119","v":"none -- but maps show a stream or other water body that is downslope from the AA and within a distance that is less than the AA's length.  If so, mark \"1\" here and SKIP TO F28 (Groundwater). "},{"$f":"F!D119","v":0},1,{"$f":"D34*E34","v":0}]
[null,null,{"$f":"F!C120","v":"no surface water flows out of the wetland except possibly during extreme events (<once per 10 years). Or, water flows only into a wetland, ditch, or lake that lacks an outlet.  If so, mark \"1\" here and SKIP TO F28 (Groundwater). "},{"$f":"F!D120","v":0},0,{"$f":"D35*E35","v":0}]
[{"$f":"F!A125","v":"F28"},{"$f":"F!B125","v":"Groundwater: Strength of Evidence"},{"$f":"F!C125","v":"Select first applicable choice. "},null,null,null,{"$f":"MAX(F37:F39)/MAX(E37:E39)","v":0},"Groundw2_","Wetlands fed by groundwater tend to remain saturated for longer in the summer, thus increasing their chances of supporting streamflow downslope."]
[null,null,{"$f":"F!C126","v":"Groundwater monitoring has demonstrated that groundwater primarily discharges to the wetland for longer periods during the year than periods when the wetland recharges the groundwater.  Or, springs are known to be present within the AA.\n\n\n"},{"$f":"F!D126","v":0},3,{"$f":"D37*E37","v":0}]
[null,null,{"$f":"F!C127","v":"One or more of the following are true: (a) the upper end of the AA is located very close to the base of (but mostly not ON) a natural slope much steeper (usually >15%) than that within the AA and longer than 100 m, OR\n(b) rust deposits (\"iron floc\"), colored precipitates, or dispersible natural oil sheen are prevalent in the AA, OR\n(c) AA water is remarkably clear in contrast to naturally stained waters typical in nearby wetlands, OR\n(d) AA is located at a geologic fault.\n\n"},{"$f":"F!D127","v":0},2,{"$f":"D38*E38","v":0}]
[null,null,{"$f":"F!C128","v":"Neither of above is true, although some groundwater may discharge to or flow through the AA.  Or groundwater influx is unknown."},{"$f":"F!D128","v":0},0,{"$f":"D39*E39","v":0}]
[{"$f":"F!A145","v":"F32"},{"$f":"F!B145","v":"Tall Woody Canopy- % of the Vegetated AA"},{"$f":"F!C145","v":"Within the vegetated part of the AA, just the woody plants taller than 3 m occupy:"},null,null,null,{"$f":"MAX(F41:F45)/MAX(E41:E45)","v":0},"WoodyPct2","Late in the growing season, woody vegetation transpires significant amounts of water, thus making that water unavailable for subsidizing stream flow.  However, woody plants can also intercept drifting snow during the winter, and  significant amounts of precipitation early during the growing season, for later use in subsidizing stream flow (Kort et al. 2012). "]
[null,null,{"$f":"F!C146","v":"<1% of the vegetated AA, or the AA lacks trees.  Enter \"1\" and SKIP to F35 (Exposed Shrub)."},{"$f":"F!D146","v":0},4,{"$f":"D41*E41","v":0}]
[null,null,{"$f":"F!C147","v":"1-25% of the vegetated AA"},{"$f":"F!D147","v":0},3,0]
[null,null,{"$f":"F!C148","v":"25-50% of the vegetated AA"},{"$f":"F!D148","v":0},2,0]
[null,null,{"$f":"F!C149","v":"50-95% of the vegetated AA"},{"$f":"F!D149","v":0},1,0]
[null,null,{"$f":"F!C150","v":">95% of the vegetated part of the AA"},{"$f":"F!D150","v":0},0,0]
[{"$f":"F!A208","v":"F44"},{"$f":"F!B208","v":"Soil Texture"},{"$f":"F!C208","v":"In parts of the AA that lack persistent water, the texture of soil in the uppermost layer is mostly:  [To determine this, use a trowel to check in at least 3 widely spaced locations, and use the soil texture key in Appendix A of the Manual]"},null,null,null,{"$f":"MAX(F47:F50)/MAX(E47:E50)","v":0},"Soil2_","Runoff ratio (the percent of precipitation that contributes to streamflow immediately after storms) is lowest for open peatland areas with thick organic horizons (0.02-0.05) due to low topographic gradients and many surface depressions capable of retaining surface water. Runoff ratio is greatest in areas with more permeable soils, at least where those areas aren't sloping. That is due partly to higher likelihood of groundwater reaching the land surface via seeps (Quinton et al. 2003)."]
[null,null,{"$f":"F!C209","v":"Loamy: includes loam, sandy loam"},{"$f":"F!D209","v":0},1,{"$f":"D47*E47","v":0}]
[null,null,{"$f":"F!C210","v":"Fines: includes silt, glacial flour, clay, clay loam, silty clay, silty clay loam, sandy clay, sandy clay loam."},{"$f":"F!D210","v":0},0,{"$f":"D48*E48","v":0}]
[null,null,{"$f":"F!C211","v":"Organic"},{"$f":"F!D211","v":0},3,{"$f":"D49*E49","v":0}]
[null,null,{"$f":"F!C212","v":"Coarse: includes sand, loamy sand, gravel, cobble, stones, boulders, fluvents, fluvaquents, riverwash."},{"$f":"F!D212","v":0},1,{"$f":"D50*E50","v":0}]
[null,null,null,null,null,null,null," "]
[null,null,"ABWRET-A FUNCTION MODEL"]
[null,null,"Stream Flow Support"]
[null,"Wetlands <10 hectares:","IF((OutNone + OutNone1>0),0, ELSE: [AVERAGE(GWDspring, FenPct, Groundw2_, Wettype2, Soil2_) + AVERAGE(Sub0Days, PPET, 1-WindSumm, 1-WetPerim2Area, OpenPonded2, 1-WetVegArea, WoodyPct2) + AVERAGE(WetPctHUC8, ElevPctileHUC8, RipFloodpl)  + AVERAGE(Depth2_, OutDur2_, WatProb)] / 4",null,null,null,{"$f":"IFERROR(IF((GT10HA=1),G55, IF((OutNone + OutNone1>0),0,  10*(AVERAGE(GWDspring, FenPct, Groundw2_, Wettype2, Soil2_) + AVERAGE(1-Sub0Days, PPET, 1-WindSumm, 1-WetPerim2Area, OpenPonded2, 1-WetVegArea, 1-WoodyPct2) + AVERAGE(WetPctHUC8, ElevPctileHUC8, RipFloodpl)  + AVERAGE(Depth2_, OutDur2_, WatProb)) / 4)),\"\")","v":""}]
[null,"Wetlands >10 hectares:","Substituted 1-OWpct, Soiltex, WetWooded",null,null,null,{"$f":"IFERROR(IF((OutNone + OutNone1>0),0,  10*(AVERAGE(GWDspring, FenPct, Groundw2_, Wettype2, SoilTex_NROE) + AVERAGE(1-Sub0Days, PPET, 1-WindSumm, 1-WetPerim2Area, 1-OWpct, 1-WetVegArea, 1-WetWooded) + AVERAGE(WetPctHUC8, ElevPctileHUC8, RipFloodpl)  + AVERAGE(Depth2_, OutDur2_, WatProb)) / 4),\"\")","v":""}]
[null,null,"ABWRET-E model ",null,null,null,null,null,"Literature Cited"]
[null,1,"IF(ChannConn + RipFloodPl = 0), then = 0",{"$f":"IF((ChannConn+RipFloodpl=0), 0, \"\")","v":0},null,null,null,null,"Doerr, S. H., C. T. Llewellyn, P. Douglas, C. P. Morley, K. A. Manwaring, and C. Haskins. 2005. Extraction of compounds associated with water repellency in sandy soils of different origin. Australian Journal of Soil Research 43:225."]
[null,2,"ELSE calculate these averages:",null,null,null,null,null,"Millar, J. B. 1971. Shoreline-area ratio as a factor in rate of water loss from small sloughs. Journal of Hydrology 14:259-284."]
[null,"a","AVERAGE(GWDspring, FenPct)",{"$f":"IFERROR(AVERAGE(GWDspring, FenPct),\"\")","v":""},null,null,null,null,"Quinton, W. L. and D. M. Gray. 2003. Subsurface drainage from organic soils in permafrost terrain: the major factors to be represented in a runoff model. In: W. Haeberli and D. Brandova, editors. Eighth International Conference on Permafrost. Glaciology and Geomorphodynamics Group, Geography Department, University of Zurich Switzerland Davos, Switzerland."]
[null,"b","AVERAGE(1-Sub0Days, PPET, 1-WindSumm, 1-WetPerim2Area, 1-OWpct,1- WetVegArea, 1-WetWooded)",{"$f":"IFERROR(AVERAGE(Sub0Days,PPET, 1-WindSumm, WetPerim2Area, 1-OWpct, WetVegArea, 1-WetWooded),\"\")","v":1},null,null,null,null,"Siegel, D. I. 1988. The recharge‐discharge function of wetlands near Juneau, Alaska: Part II. Geochemical investigations. Ground Water 26:580-586."]
[null,"c","AVERAGE(WetPctHUC8, ElevPctileHUC8)",{"$f":"IFERROR(AVERAGE(WetPctHUC8, ElevPctileHUC8),\"\")","v":""}]
[null,3,"10*MAX [#1, AVERAGE(WatProb, a, b, c)]",{"$f":"10*MAX(D57, AVERAGE(WatProb, D59:D61))","v":10}]
[]
[null,null,"ABWRET-E with substitutions:"]
[null,1,"IF(OutNone+OutNone1>0), then =0",{"$f":"IF((OutNone+OutNone1>0), 0, \"\")","v":""}]
[null,2,"ELSE calculate these averages:"]
[null,"a","AVERAGE(GWDspring, FenPct)",{"$f":"IFERROR(AVERAGE(GWDspring, FenPct),\"\")","v":""}]
[null,"b","AVERAGE(1-Sub0Days, PPET, 1-WindSumm, 1-WetPerim2Area, OpenPonded2, 1-WetVegArea, 1-WoodyPct2)",{"$f":"IFERROR(AVERAGE(1-Sub0Days,PPET, 1-WindSumm,1- WetPerim2Area, OpenPonded2, 1-WetVegArea, 1-WoodyPct2),\"\")","v":0.83333333333333337}]
[null,"c","AVERAGE(WetPctHUC8, ElevPctileHUC8)",{"$f":"IFERROR(AVERAGE(WetPctHUC8, ElevPctileHUC8),\"\")","v":""}]
[null,3,"10*MAX [#1, AVERAGE(WatProb, a, b, c)]",{"$f":"10*MAX(D65, AVERAGE(WatProb, D67:D69))","v":8.3333333333333339}]
[]
[]
[]
[]
[]
[]
[]
[]
[]
[]
[]
[]
[]
[]
[]
[]
[]
[]
[]
[]
[]
[]
[]
[]
[]
[]
[]
[]
[]
[]
[null,null,null,null,null,null,"*"]

{"sheet":"WC","index":11,"n_rows":95,"n_cols":11,"rows_kept":95,"cut":false,"hidden":false,"merged":[[75,3,76,6],[48,0,54,0],[15,8,20,8],[15,1,20,1],[15,0,20,0],[21,8,27,8],[48,8,54,8],[40,1,47,1],[40,8,47,8],[48,1,54,1],[40,0,47,0],[40,7,47,7],[48,7,54,7],[55,8,60,8],[55,0,60,0],[55,1,60,1],[10,7,14,7],[15,7,20,7],[21,7,27,7],[0,4,0,7],[34,8,39,8],[28,8,33,8],[10,8,14,8],[34,7,39,7],[28,7,33,7],[0,0,0,1],[34,1,39,1],[21,0,27,0],[28,0,33,0],[34,0,39,0],[21,1,27,1],[28,1,33,1],[10,0,14,0],[10,1,14,1],[61,8,64,8],[61,1,64,1],[61,0,64,0],[55,7,60,7],[61,7,64,7]]}
["Water                         Cooling",null,"The effectiveness for maintaining or reducing temperature of downgradient waters.","WC",null,null,null,null,"The model does not address the ecological need for cooling or maintaining temperatures of streams at a particular location, as would be implied partly by the presence of coldwater fish and the closeness of ambient summer temperatures to physiological thresholds of those fish. The model also does not address the benefits of cooled water that relate to its ability to hold more dissolved oxygen, which in turn supports better processing of many pollutants."]
["#","Function Indicators from Estimator","Scoring Notes",null,null,null,"Normalised Score","Indicator Abbreviation or Formula","Rationale"]
[{"$f":"OF!A5","v":"OF4"},{"$f":"OF!C5","v":"Channel Connection"},null,null,null,null," ","ChannConn","Wetlands that have no outflow are likely to have only minimal effect on temperature of downslope water bodies."]
[{"$f":"OF!A15","v":"OF14"},{"$f":"OF!C15","v":"% of the Wetland that is Fen"},null,null,null,null,{"$f":"IF((FenPct=\"\"),\"\",FenPct)","v":""},"FenPct","Fens are groundwater discharge areas.  The discharging groundwater in most cases is cooler than receiving surface waters."]
[{"$f":"OF!A19","v":"OF18"},{"$f":"OF!C19","v":"Groundwater Discharge Area or Spring"},null,null,null,null,{"$f":"IF((GWDspring=\"\"),\"\",GWDspring)","v":""},"GWDspring","See above."]
[{"$f":"OF!A23","v":"OF22"},{"$f":"OF!C23","v":"L/G Index (Residence Time)"},"Inverse",null,null,null,{"$f":"IF((LGIndex=\"\"),\"\",1-LGIndex)","v":""},"LGIndex","Longer retention time means more time for stagnant water to reach air temperature or heat further as a result of solar exposure."]
[{"$f":"OF!A43","v":"OF42"},{"$f":"OF!C43","v":"Riparian or Floodway Location"},null,null,null,null,{"$f":"IF((LGIndex=\"\"),\"\",LGIndex)","v":""},"RipFloodpl","Wetlands that are not connected to downgradient waters at least seasonally have only minimal effect on temperature of those water bodies."]
[{"$f":"OF!A61","v":"OF60"},{"$f":"OF!C61","v":"Water Permanence Probability"},"In calculations, is excluded automatically (cell goes blank) if AA is not a groundwater discharge area or spring. ",null,null,null,{"$f":"IF((WatProb=\"\"),\"\", IF((GWDspring=0),\"\", WatProb))","v":""},"WatProb","Surface water that persists in a wetland for longer into the summer can continue for longer to subsidize downgradient water bodies with water that potentially is cooler."]
[{"$f":"OF!A70","v":"OF69"},{"$f":"OF!C70","v":"% of Wetland Classified as Swamp or Forested (macro scale)"},null,null,null,null,{"$f":"IF((WetWooded=\"\"),\"\",WetWooded)","v":""},"WetWooded","Woody vegetation is assumed to provide more shade than herbaceous, and shade cools or helps maintain temperature of surface waters (e.g., Rounds 2007)."]
["#","Function Indicators from Onsite Visit","Categorical Choices","Data","Weight","Data  x  Weight","Normalised Score","Indicator Abbreviation or Formula","Rationale & Scoring Notes"]
[{"$f":"F!A6","v":"F1"},{"$f":"F!B6","v":"Wetland Type - Predominant"},{"$f":"F!C6","v":"Most of the vegetated part of the AA (wetland Assessment Area) is a (select ONE):"},null,null,null,{"$f":"MAX(F12:F15)/MAX(E12:E15)","v":0},"WclassDom7","The weights assigned to the wetland classes reflect the likelihood of there being extensive shade and/or discharging groundwater, which both cool or help maintain water temperature."]
[null,null,{"$f":"F!C7","v":"Wooded Swamp"},{"$f":"F!D7","v":0},3,{"$f":"D12*E12","v":0}]
[null,null,{"$f":"F!C8","v":"Bog"},{"$f":"F!D8","v":0},2,{"$f":"D13*E13","v":0}]
[null,null,{"$f":"F!C9","v":"Fen"},{"$f":"F!D9","v":0},4,{"$f":"D14*E14","v":0}]
[null,null,{"$f":"F!C10","v":"Marsh or Shallow Open Water"},{"$f":"F!D10","v":0},1,{"$f":"D15*E15","v":0}]
[{"$f":"F!A11","v":"F2"},{"$f":"F!B11","v":"Wetland Types - Subordinate"},{"$f":"F!C11","v":"Mark all other vegetated wetland types in the AA that occupy more than 1 hectare or more than 1% of the vegetated AA.  Do not mark the predominant type again.  If AA is larger than 1 ha, see preliminary imagery-based answer provided by AESRD, but field-verify."},null,null,null,{"$f":"IF((D21=1),\"\",MAX(F17:F20)/MAX(E17:E20))","v":0},"WclassSub7","In calculations, is excluded automatically (cell goes blank) if AA contains no other wetland types except the dominant one noted above -- in which case only that one drives the score."]
[null,null,{"$f":"F!C12","v":"Wooded Swamp"},{"$f":"F!D12","v":0},3,{"$f":"D17*E17","v":0}]
[null,null,{"$f":"F!C13","v":"Bog"},{"$f":"F!D13","v":0},2,{"$f":"D18*E18","v":0}]
[null,null,{"$f":"F!C14","v":"Fen"},{"$f":"F!D14","v":0},4,{"$f":"D19*E19","v":0}]
[null,null,{"$f":"F!C15","v":"Marsh or Shallow Open Water"},{"$f":"F!D15","v":0},1,{"$f":"D20*E20","v":0}]
[null,null,{"$f":"F!C16","v":"no types other than the predominant one in F1 meet the area threshold."},{"$f":"F!D16","v":0}]
[{"$f":"F!A17","v":"F3"},{"$f":"F!B17","v":"% Saturated Only"},{"$f":"F!C17","v":"The percentage of the AA that never contains surface water during an average year (that is, except perhaps for a few hours after snowmelt or rainstorms), but which is still a wetland, is:"},null,null,null,{"$f":"MAX(F23:F28)/MAX(E23:E28)","v":0},"SatPct7","When water remains entirely belowground, water temperatures in summer remain cooler than if exposed aboveground."]
[null,null,{"$f":"F!C18","v":"less than 1%, or <0.01 hectare (about 10 m on a side) never has surface water.  In other words, all or nearly all of the AA is inundated permanently or at least seasonally."},{"$f":"F!D18","v":0},0,{"$f":"D23*E23","v":0}]
[null,null,{"$f":"F!C19","v":"1-25% of the AA never contains surface water."},{"$f":"F!D19","v":0},1,0]
[null,null,{"$f":"F!C20","v":"25-50% of the AA never contains surface water."},{"$f":"F!D20","v":0},2,0]
[null,null,{"$f":"F!C21","v":"50-99% of the AA never contains surface water."},{"$f":"F!D21","v":0},3,0]
[null,null,{"$f":"F!C22","v":">99% of the AA never contains surface water, except for water flowing in channels and/or in pools that occupy <1% of the AA. SKIP to F26 (Channel Connection & Outflow Duration)"},{"$f":"F!D22","v":0},4,0]
[null,null,{"$f":"F!C23","v":">99% of the AA never contains surface water, and AA is not intersected by channels that have flow, not even for a few days per year. SKIP to F26."},{"$f":"F!D23","v":0},5,0]
[{"$f":"F!A31","v":"F5"},{"$f":"F!B31","v":"% of Summertime Water That Is Shaded"},{"$f":"F!C31","v":"At mid-day during the warmest time of year, the area of surface water within the AA that is shaded (by emergent or woody vegetation, incised channels, streambanks, or other features also present within the AA) is:"},null,null,null,{"$f":"IF((AllSat+AllSat1>0),\"\",IF((NoPersis=1),\"\",(MAX(F30:F34)/MAX(E30:E34))))","v":0},"Shade7","Shade from vegetation and other features is an important factor in cooling surface water and runoff before it reaches water bodies farther downstream (e.g., Rounds 2007).  A study of many Seattle-area wetlands found that summertime temperatures ranged higher in wetlands that were characterized by relatively large open pools that lacked shade (Reinelt & Horner 1990). In calculations, is excluded automatically (cell goes blank) if wetland never has surface water during an average year or if water is present only seasonally."]
[null,null,{"$f":"F!C32","v":"<5% of the water is shaded, or no surface water is present then."},{"$f":"F!D32","v":0},0,{"$f":"D30*E30","v":0}]
[null,null,{"$f":"F!C33","v":"5-25% of the water is shaded"},{"$f":"F!D33","v":0},1,{"$f":"D31*E31","v":0}]
[null,null,{"$f":"F!C34","v":"25-50% of the water is shaded"},{"$f":"F!D34","v":0},2,{"$f":"D32*E32","v":0}]
[null,null,{"$f":"F!C35","v":"50-75% of the water is shaded"},{"$f":"F!D35","v":0},3,{"$f":"D33*E33","v":0}]
[null,null,{"$f":"F!C36","v":">75% of the water is shaded"},{"$f":"F!D36","v":0},4,{"$f":"D34*E34","v":0}]
[{"$f":"F!A52","v":"F10"},{"$f":"F!B52","v":"Predominant Depth Class"},{"$f":"F!C52","v":"During most of the time when water is present, its depth in most of the area is: [Note: This is not asking for the maximum depth.]"},null,null,null,{"$f":"IF((AllSat+AllSat1>0),\"\",MAX(F36:F40)/MAX(E36:E40))","v":0},"Depth7","Wetlands with greater water depth overall tend to have cooler outflows (depending on elevation of the outlet) because water depth provides insulation from solar warming. In calculations, is excluded automatically (cell goes blank) if wetland never has surface water during an average year. Also is excluded automatically if wetland is <0.01 ha."]
[null,null,{"$f":"F!C53","v":"<10 cm deep (but >0)"},{"$f":"F!D53","v":0},0,{"$f":"D36*E36","v":0}]
[null,null,{"$f":"F!C54","v":"10 - 50 cm deep"},{"$f":"F!D54","v":0},1,{"$f":"D37*E37","v":0}]
[null,null,{"$f":"F!C55","v":"0.5 - 1 m deep"},{"$f":"F!D55","v":0},2,{"$f":"D38*E38","v":0}]
[null,null,{"$f":"F!C56","v":"1 - 2 m deep"},{"$f":"F!D56","v":0},4,{"$f":"D39*E39","v":0}]
[null,null,{"$f":"F!C57","v":">2 m deep.  True for many fringe wetlands."},{"$f":"F!D57","v":0},6,{"$f":"D40*E40","v":0}]
[{"$f":"F!A62","v":"F12"},{"$f":"F!B62","v":"% of Water Ponded vs. Flowing "},{"$f":"F!C62","v":"The percentage of the AA's surface water that is ponded (stagnant, or flows so slowly that fine sediment is not held in suspension) during most of the time it is present, and which is either open or shaded by emergent vegetation is:"},null,null,null,{"$f":"IF((AllSat+AllSat1>0),\"\", IF((SmallAA=1),\"\", MAX(F42:F48)/MAX(E42:E48)))","v":0},"ISOdry7","Where most of the surface water is ponded, it is more likely to be heated by the sun than if distributed in the channels or residing underground.  In calculations, is excluded automatically (cell goes blank) if wetland never has surface water during an average year.  Also is excluded automatically if wetland is <0.01 ha."]
[null,null,{"$f":"F!C63","v":"<1% or none, or occupies <0.01 hectare cumulatively.  Nearly all water is flowing.  Enter \"1\" and SKIP to F21 (Stained Surface Water)."},{"$f":"F!D63","v":0},6,{"$f":"D42*E42","v":0}]
[null,null,{"$f":"F!C64","v":"1-5% of the water, and mainly in small pools.  The rest is flowing."},{"$f":"F!D64","v":0},5,0]
[null,null,{"$f":"F!C65","v":"1-5% of the water, and mainly in a single large pool or pond.  The rest is flowing."},{"$f":"F!D65","v":0},4,0]
[null,null,{"$f":"F!C66","v":"5-30% of the water"},{"$f":"F!D66","v":0},3,0]
[null,null,{"$f":"F!C67","v":"30-70% of the water"},{"$f":"F!D67","v":0},2,0]
[null,null,{"$f":"F!C68","v":"70-95% of the water"},{"$f":"F!D68","v":0},1,0]
[null,null,{"$f":"F!C69","v":">95% of the water.  Little or no visibly flowing water within the AA."},{"$f":"F!D69","v":0},0,0]
[{"$f":"F!A71","v":"F14"},{"$f":"F!B71","v":"% of Ponded Water That Is Open "},{"$f":"F!C71","v":"In ducks-eye aerial view, the percentage of the ponded water that is open (lacking emergent vegetation during most of the growing season, and unhidden by a forest or shrub canopy) is:"},null,null,null,{"$f":"IF((AllSat+AllSat1>0),\"\",IF((NoPonded=1),\"\",MAX(F50:F55)/MAX(E50:E55)))","v":0},"OpenPonded7","Ponded water that is open and unvegetated it is more likely to be heated by the sun.  In calculations, is excluded automatically (cell goes blank) if wetland never has surface water during an average year.  Also is excluded automatically if wetland has no ponded water."]
[null,null,{"$f":"F!C72","v":"<1% or none, or largest pool occupies <0.01 hectares.  Enter \"1\" and SKIP to F20 (Floating Algae & Duckweed)."},{"$f":"F!D72","v":0},5,0]
[null,null,{"$f":"F!C73","v":"1-5% of the ponded water.  Enter \"1\" and SKIP to F20."},{"$f":"F!D73","v":0},4,0]
[null,null,{"$f":"F!C74","v":"5-30% of the ponded water."},{"$f":"F!D74","v":0},3,0]
[null,null,{"$f":"F!C75","v":"30-70% of the ponded water."},{"$f":"F!D75","v":0},2,0]
[null,null,{"$f":"F!C76","v":"70-99% of the ponded water."},{"$f":"F!D76","v":0},1,0]
[null,null,{"$f":"F!C77","v":"100% of the ponded water. "},{"$f":"F!D77","v":0},0,0]
[{"$f":"F!A115","v":"F26"},{"$f":"F!B115","v":"Channel Connection & Outflow Duration"},{"$f":"F!C115","v":"The most persistent surface water connection (outlet channel or pipe, ditch, or overbank water exchange) between the AA and the closest off-site downslope water body is:"},null,null,null,{"$f":"MAX(F57:F61)/MAX(E57:E61)","v":0},"OutDur7","Wetlands that have no outflow are likely to have only minimal effect on temperature of other water bodies."]
[null,null,{"$f":"F!C116","v":"persistent (>9 months/year, including times when frozen)"},{"$f":"F!D116","v":0},5,{"$f":"D57*E57","v":0}]
[null,null,{"$f":"F!C117","v":"seasonal (14 days to 9 months/year, not necessarily consecutive, including times when frozen)"},{"$f":"F!D117","v":0},2,{"$f":"D58*E58","v":0}]
[null,null,{"$f":"F!C118","v":"temporary (<14 days, not necessarily consecutive -- must be unfrozen)"},{"$f":"F!D118","v":0},1,{"$f":"D59*E59","v":0},null,null,null,null," "]
[null,null,{"$f":"F!C119","v":"none -- but maps show a stream or other water body that is downslope from the AA and within a distance that is less than the AA's length.  If so, mark \"1\" here and SKIP TO F28 (Groundwater). "},{"$f":"F!D119","v":0},0,{"$f":"D60*E60","v":0}]
[null,null,{"$f":"F!C120","v":"no surface water flows out of the wetland except possibly during extreme events (<once per 10 years). Or, water flows only into a wetland, ditch, or lake that lacks an outlet.  If so, mark \"1\" here and SKIP TO F28 (Groundwater). "},{"$f":"F!D120","v":0},0,{"$f":"D61*E61","v":0}]
[{"$f":"F!A125","v":"F28"},{"$f":"F!B125","v":"Groundwater: Strength of Evidence"},{"$f":"F!C125","v":"Select first applicable choice. "},null,null,null,{"$f":"MAX(F63:F65)/MAX(E63:E65)","v":0},"Gwater7","Groundwater discharging into wetlands supports a wetland's capacity to cool surface runoff during summer because groundwater in most cases is cooler than surface water during that time (Mellina et al. 2002). For example, in higher-gradient intermittent headwater streams, the cooling effect of groundwater may be greater than that of shade (Janisch et al. 2012). Cooling effects may extend 50 m to 4 km downstream from an individual source of cooler water, depending on the temperature and discharge rate from the source relative to those of the receiving waters (Caldwell et al. 1991, Lewis et al. 2000)."]
[null,null,{"$f":"F!C126","v":"Groundwater monitoring has demonstrated that groundwater primarily discharges to the wetland for longer periods during the year than periods when the wetland recharges the groundwater.  Or, springs are known to be present within the AA.\n\n\n"},{"$f":"F!D126","v":0},3,{"$f":"D63*E63","v":0}]
[null,null,{"$f":"F!C127","v":"One or more of the following are true: (a) the upper end of the AA is located very close to the base of (but mostly not ON) a natural slope much steeper (usually >15%) than that within the AA and longer than 100 m, OR\n(b) rust deposits (\"iron floc\"), colored precipitates, or dispersible natural oil sheen are prevalent in the AA, OR\n(c) AA water is remarkably clear in contrast to naturally stained waters typical in nearby wetlands, OR\n(d) AA is located at a geologic fault.\n\n"},{"$f":"F!D127","v":0},2,{"$f":"D64*E64","v":0}]
[null,null,{"$f":"F!C128","v":"Neither of above is true, although some groundwater may discharge to or flow through the AA.  Or groundwater influx is unknown."},{"$f":"F!D128","v":0},0,{"$f":"D65*E65","v":0}]
[]
[null,null,"Shading [SHADE]"]
[null,null,"AVERAGE(WclassDom7, WclassSub7, SatPct7, Shade7)",null,null,null,{"$f":"IFERROR(AVERAGE(WclassDom7, WclassSub7, SatPct7, Shade7),\"\")","v":0}]
[]
[null,null,"Water Heating [SOLAR]"]
[null,"Wetlands <10 hectares:","AVERAGE(Depth7, ISOdry7, OpenPonded7, WetWooded)",null,null,null,{"$f":"IF((GT10HA=1),G72, IFERROR(AVERAGE(Depth7, ISOdry7, OpenPonded7, 1-WetWooded),\"\"))","v":0.25}]
[null,"Wetlands >10 hectares:","Substituted OWpct.  Added 1-LGindex.",null,null,null,{"$f":"IFERROR(AVERAGE(Depth7, ISOdry7, OWpct, WetWooded,1-LGIndex),\"\")","v":0.33333333333333331}]
[]
[null,null,"Groundwater Input [GWin]"]
[null,null,"AVERAGE(Gwater7, GWDspring, FenPct)",null,null,null,{"$f":"IFERROR(AVERAGE(Gwater7, GWDspring, FenPct),\"\")","v":0}]
[]
[null,null,"Export [OUT]"]
[null,null,"AVERAGE(OutDur7, RipFloodPl, WatProb) ",null,null,null,{"$f":"IFERROR(AVERAGE(OutDur7, RipFloodpl),\"\")","v":0}]
[]
[null,null,"ABWRET-A FUNCTION MODEL"]
[null,null,"Water Cooling"]
[null,null,"IF((OutNone + OutNone1>0),0, ELSE: 10*AVERAGE(SHADE, SOLAR, GWin, OUT)",null,null,null,{"$f":"IF((OutNone + OutNone1>0),10, 10*AVERAGE(SHADE1A, SOLAR1A, GWIN1A, OUT7A))","v":0.625}]
[" ",null,null,null,null,null,null,null,"Literature Cited"]
[null,null,null,null,null,null,null,null,"Brosofske, K. D., J. Chen, R. J. Naiman, and J. F. Franklin. 1997. Harvesting effects on microclimatic gradients from small streams to uplands in western Washington. Ecological Applications 7:1188-1200."]
[null,null,null,null,null,null,null,null,"Caldwell, J. E., K. Doughty, and K. Sullivan. 1991. Evaluation of downstream temperature effects of type 4/5 waters.Timber/Fish/Wildlife Rep. No. TFW -WQ5-91-004. Washington Department of Natural Resources, Olympia, WA."]
[null,null,null,null,null,null,null,null,"Gomi, T., R. D. Moore, and A. S. Dhakal. 2006. Headwater stream temperature response to clear-cut harvesting with different riparian treatments, coastal British Columbia, Canada. Water Resources Research 42:WO8437."]
[null,null,null,null,null,null,null,null,"Janisch, J. E., S. M. Wondzell, and W. J. Ehinger. 2012. Headwater stream temperature: Interpreting response after logging, with and without riparian buffers, Washington, USA. Forest Ecology and Management 270:302-313."]
[null,null,null,null,null,null,null,null,"Lewis, D., M. J. Singer, R. A. Dahlgren, and K. W. Tate. 2000. Hydrology in a California oak woodland watershed: a 17-year study. Journal of Hydrology 240:106-117."]
[null,null,null,null,null,null,null,null,"Meleason, M. A. and J. M. Quinn. 2004. Influence of riparian buffer width on air temperature at Whangapoua Forest, Coromandel Peninsula, New Zealand. Forest Ecology and Management 191:365-371."]
[null,null,null,null,null,null,null,null,"Mellina, E., R. D. Moore, S. G. Hinch, J. S. Macdonald, and G. Pearson. 2002. Stream temperature responses to clearcut logging in British Columbia: the moderating influences of groundwater and headwater lakes. Canadian Journal of Fisheries and Aquatic Sciences 59:1886-1900."]
[null,null,null,null,null,null,null,null,"Nelitz, M. A., E. A. MacIsaac, and R. M. Peterman. 2007. A science-based approach for identifying temperature-sensitive streams for rainbow trout. North American Journal of Fisheries Management 27:405-424."]
[null,null,null,null,null,null,null,null,"Reinelt, L. E. and R. R. Horner. 1990. Characterization of the Hydrology and Water Quality of Palustrine Wetlands Affected by Urban Stormwater. King County Resource Planning Section, Seattle, WA."]
[null,null,null,null,null,null,null,null,"Rounds, S. A. 2007. Temperature Effects of Point Sources, Riparian Shading, and Dam Operations on the Willamette River, Oregon. Scientific Investigations Report 2007–5185. U.S. Department of the Interior, U.S. Geological Survey, Portland, OR."]
[null,null,null,null,null,null,null,null,"Sridhar, V., A. L. Sansone, J. LaMarche, T. Dubin, and D. P. Lettenmaier. 2004. Prediction of stream temperature in forested watersheds. Journal of the American Water Resources Association 40:197-213."]
[null,null,null,null,null,null,null,null,"Stephenson, J. M. and A. Morin. 2009. Covariation of stream community structure and biomass of algae, invertebrates and fish with forest cover at multiple spatial scales. Freshwater Biology 54:2139-2154."]

{"sheet":"SR","index":12,"n_rows":123,"n_cols":9,"rows_kept":123,"cut":false,"hidden":false,"merged":[[27,7,34,7],[35,7,41,7],[54,7,57,7],[58,7,63,7],[64,7,69,7],[58,8,63,8],[74,8,78,8],[84,1,87,1],[84,0,87,0],[70,8,73,8],[64,8,69,8],[58,1,63,1],[84,8,87,8],[79,8,83,8],[58,0,63,0],[79,0,83,0],[70,1,73,1],[79,1,83,1],[64,1,69,1],[74,0,78,0],[64,0,69,0],[70,0,73,0],[88,8,92,8],[88,1,92,1],[88,0,92,0],[74,1,78,1],[88,7,92,7],[70,7,73,7],[74,7,78,7],[79,7,83,7],[84,7,87,7],[10,0,15,0],[35,8,41,8],[27,8,34,8],[54,1,57,1],[42,8,47,8],[35,1,41,1],[27,1,34,1],[42,1,47,1],[48,8,53,8],[54,0,57,0],[27,0,34,0],[48,0,53,0],[48,1,53,1],[35,0,41,0],[10,7,15,7],[48,7,53,7],[112,0,113,0],[0,0,0,1],[42,0,47,0],[21,1,26,1],[10,8,15,8],[16,0,20,0],[10,1,15,1],[21,8,26,8],[16,8,20,8],[16,1,20,1],[21,0,26,0],[0,4,0,7],[16,7,20,7],[21,7,26,7],[42,7,47,7],[54,8,57,8]]}
["Sediment             Retention                                        and                    Stabilization",null,"The effectiveness for intercepting and filtering suspended inorganic sediments, thus allowing their deposition, as well as reducing energy of waves and currents, resisting excessive erosion, and stabilizing underlying sediments or soil.","SR",null,null,null,null,"The model does not address the ecological need for keeping suspended sediment out of streams at a particular location, as would be implied partly by the presence of sensitive aquatic life in those streams.  The model also does not address the potential harm to wetland organisms that occurs when excessive amounts of sediment  smother plants and animals within a wetland.  Nor does the model address the loss in water storage space that occurs when sediment is deposited and retained.  The model does not address the potential positive benefits of trapping and depositing sediment along the deepwater margin of lakeshore wetlands, which can gradually increase the area of wetlands."]
["#","Function Indicators from Estimator","Scoring Notes",null,null,null,"Normalised Score","Indicator Abbreviation or Formula","Rationale"]
[{"$f":"OF!A5","v":"OF4"},{"$f":"OF!C5","v":"Channel Connection"},null,null,null,null,{"$f":"IF((ChannConn=\"\"),\"\",ChannConn)","v":""},"ChannConn","Wetlands that lack an outlet (never have any outflow) retain all sediment that enters them unless it is eroded by wind."]
[{"$f":"OF!A23","v":"OF22"},{"$f":"OF!C23","v":"L/G Index (Residence Time)"},null,null,null,null,{"$f":"IF((LGIndex=\"\"),\"\",LGIndex)","v":""},"LGIndex","Longer flow paths within a wetland allow more time and opportunity for suspended sediments to be deposited."]
[{"$f":"OF!A28","v":"OF27"},{"$f":"OF!C28","v":"Interspersion Index for Internal Water & Vegetation (macroscale)"},null,null,null,null,{"$f":"IF((MixWaterVeg=\"\"),\"\",MixWaterVeg)","v":""},"MixWaterVeg","Greater interspersion of vegetation with open water is likely to support more sediment retention because it implies more contact between plants that trap sediment and the sediment-bearing water. "]
[{"$f":"OF!A31","v":"OF30"},{"$f":"OF!C31","v":"% of AA that is Open Water (macro scale)"},"Inverse",null,null,null,{"$f":"IF((OWpct=\"\"),\"\",1-OWpct)","v":""},"OWpct","Open water areas are more prone to wind that can mix of bottom sediments, resuspending the sediment and resulting in export if an outlet is present. When there is proportionally more vegetation than open water, that provides potential for trapping suspended sediment and stabilizing sediment already deposited. "]
[{"$f":"OF!A46","v":"OF45"},{"$f":"OF!C46","v":"% Slope "},null,null,null,null,{"$f":"IF((SlopeBuffer=\"\"),\"\",SlopeBuffer)","v":""},"SlopeBuffer","The presence of steep slopes near a wetland suggests that water residence time in the associated wetland may also be short, thus reducing its potential for retaining sediment.  However, if the wetland is large, slope angle is unlikely to have much effect on water residence time within that wetland. "]
[{"$f":"OF!A52","v":"OF51"},{"$f":"OF!C52","v":"Subzero Days"},"Inverse",null,null,null,{"$f":"IF((Sub0Days=\"\"),\"\",1-Sub0Days)","v":""},"Sub0Days","Wetlands frozen later into the spring (as indicated by Subzero Days) are less able to retain sediment suspended in snowmelt runoff. "]
[{"$f":"OF!A69","v":"OF68"},{"$f":"OF!C69","v":"Wetland Vegetated Area"},null,null,null,null,{"$f":"IF((WetVegArea=\"\"),\"\",WetVegArea)","v":""},"WetVegArea","The absolute size of the vegetated area correlates with increased sediment trapping and stabilization potential, and is sometimes independent of the proportion of the wetland that is vegetated.  Larger vegetated areas imply longer retention times that support deposition and retention.  "]
["#","Function Indicators from Onsite Visit","Categorical Choices","Data","Weight","Data  x  Weight","Normalised Score","Indicator Abbreviation or Formula","Rationale & Scoring Notes"]
[{"$f":"F!A39","v":"F8"},{"$f":"F!B39","v":"% Flooded Only Seasonally"},{"$f":"F!C39","v":"The percentage of the AA that is covered by surface water only during the wettest time of year (and for >2 consecutive days during that time) is:"},null,null,null,{"$f":"IF((AllSat+AllSat1>0),\"\",MAX(F12:F16)/MAX(E12:E16))","v":0},"SeasPct2","As a wetland's surface water area expands seasonally, water velocity is often reduced due to increased friction, and material suspended in the expanding water body is more likely to be deposited.  In calculations, is excluded automatically (cell goes blank) if wetland never has surface water during an average year. "]
[null,null,{"$f":"F!C40","v":"<1%. "},{"$f":"F!D40","v":0},0,{"$f":"D12*E12","v":0}]
[null,null,{"$f":"F!C41","v":"1-25% "},{"$f":"F!D41","v":0},1,{"$f":"D13*E13","v":0}]
[null,null,{"$f":"F!C42","v":"25-50% "},{"$f":"F!D42","v":0},2,{"$f":"D14*E14","v":0}]
[null,null,{"$f":"F!C43","v":"50-95% "},{"$f":"F!D43","v":0},3,{"$f":"D15*E15","v":0}]
[null,null,{"$f":"F!C44","v":">95% "},{"$f":"F!D44","v":0},4,{"$f":"D16*E16","v":0}]
[{"$f":"F!A45","v":"F9"},{"$f":"F!B45","v":"Annual Water Fluctuation Range"},{"$f":"F!C45","v":"The annual fluctuation in surface water level within most of the parts of the AA that contain surface water is:"},null,null,null,{"$f":"IF((AllSat+AllSat1>0),\"\",IF((NoSeasonal=1),\"\",MAX(F18:F21)/MAX(E18:E21)))","v":0},"Fluc2","Suspended sediment is more likely to be filtered and stranded in vegetation if water levels fluctuate. However, in some soil types, large water level fluctuations (especially if artificially induced) cause erosion that results in more sediment being exported than retained. In calculations, is excluded automatically (cell goes blank) if wetland never has surface water during an average year or if surface water is permanent (i.e., must have at least a seasonal-only zone in order to have water fluctuation)."]
[null,null,{"$f":"F!C46","v":"<10 cm change (stable) "},{"$f":"F!D46","v":0},1,{"$f":"D18*E18","v":0}]
[null,null,{"$f":"F!C47","v":"10 cm - 50 cm change"},{"$f":"F!D47","v":0},2,{"$f":"D19*E19","v":0}]
[null,null,{"$f":"F!C49","v":"1-2 m change"},{"$f":"F!D49","v":0},3,{"$f":"D20*E20","v":0}]
[null,null,{"$f":"F!C50","v":">2 m change"},{"$f":"F!D50","v":0},4,{"$f":"D21*E21","v":0}]
[{"$f":"F!A52","v":"F10"},{"$f":"F!B52","v":"Predominant Depth Class"},{"$f":"F!C52","v":"During most of the time when water is present, its depth in most of the area is: [Note: This is not asking for the maximum depth.]"},null,null,null,{"$f":"IF((AllSat+AllSat1>0),\"\", IF((SmallAA=1),\"\", MAX(F23:F27)/MAX(E23:E27)))","v":0},"DepthC2","Deeper waters usually imply slower water velocity, longer water detention time, more space for storing deposited sediments over time, and reduced likelihood of deposited sediments being resuspended by wind mixing or currents (Evans & Rigler 1983, Nolen et al. 1985). However, vegetation density is usually greater in shallow wetlands, providing other opportunities to filter and stabilize (with roots systems) suspended sediments. In calculations, is excluded automatically (cell goes blank) if wetland never has surface water during an average year. Also is excluded automatically if wetland is <0.01 ha."]
[null,null,{"$f":"F!C53","v":"<10 cm deep (but >0)"},{"$f":"F!D53","v":0},1,{"$f":"D23*E23","v":0}]
[null,null,{"$f":"F!C54","v":"10 - 50 cm deep"},{"$f":"F!D54","v":0},2,{"$f":"D24*E24","v":0}]
[null,null,{"$f":"F!C55","v":"0.5 - 1 m deep"},{"$f":"F!D55","v":0},3,{"$f":"D25*E25","v":0}]
[null,null,{"$f":"F!C56","v":"1 - 2 m deep"},{"$f":"F!D56","v":0},4,{"$f":"D26*E26","v":0}]
[null,null,{"$f":"F!C57","v":">2 m deep.  True for many fringe wetlands."},{"$f":"F!D57","v":0},5,{"$f":"D27*E27","v":0}]
[{"$f":"F!A62","v":"F12"},{"$f":"F!B62","v":"% of Water Ponded vs. Flowing "},{"$f":"F!C62","v":"The percentage of the AA's surface water that is ponded (stagnant, or flows so slowly that fine sediment is not held in suspension) during most of the time it is present, and which is either open or shaded by emergent vegetation is:"},null,null,null,{"$f":"IF((AllSat+AllSat1>0),\"\", IF((SmallAA=1),\"\", MAX(F29:F35)/MAX(E29:E35)))","v":0},"_Iso2","Ponding allows more time for suspended sediment to settle out.  In calculations, is excluded automatically (cell goes blank) if wetland never has surface water during an average year. Also is excluded automatically if wetland is <0.01 ha."]
[null,null,{"$f":"F!C63","v":"<1% or none, or occupies <0.01 hectare cumulatively.  Nearly all water is flowing.  Enter \"1\" and SKIP to F21 (Stained Surface Water)."},{"$f":"F!D63","v":0},0,{"$f":"D29*E29","v":0}]
[null,null,{"$f":"F!C64","v":"1-5% of the water, and mainly in small pools.  The rest is flowing."},{"$f":"F!D64","v":0},2,0]
[null,null,{"$f":"F!C65","v":"1-5% of the water, and mainly in a single large pool or pond.  The rest is flowing."},{"$f":"F!D65","v":0},2,0]
[null,null,{"$f":"F!C66","v":"5-30% of the water"},{"$f":"F!D66","v":0},3,0]
[null,null,{"$f":"F!C67","v":"30-70% of the water"},{"$f":"F!D67","v":0},4,0]
[null,null,{"$f":"F!C68","v":"70-95% of the water"},{"$f":"F!D68","v":0},5,0]
[null,null,{"$f":"F!C69","v":">95% of the water.  Little or no visibly flowing water within the AA."},{"$f":"F!D69","v":0},6,0]
[{"$f":"F!A71","v":"F14"},{"$f":"F!B71","v":"% of Ponded Water That Is Open "},{"$f":"F!C71","v":"In ducks-eye aerial view, the percentage of the ponded water that is open (lacking emergent vegetation during most of the growing season, and unhidden by a forest or shrub canopy) is:"},null,null,null,{"$f":"IF((AllSat+AllSat1>0),\"\", IF((NoPonded=1),\"\", IF((SmallAA=1), \"\", MAX(F37:F42)/MAX(E37:E42))))","v":0},"OpenPonded2","As the proportionate area of emergent and other aquatic plants increases, current velocity may be reduced (depending on the distribution of the plants relative to flow paths), and a larger proportion of the sediment may be intercepted, particularly if the wetland is not narrow. In calculations, is excluded automatically (cell goes blank) if wetland never has surface water during an average year. Also is excluded automatically if wetland has no ponded water or is <0.01 ha."]
[null,null,{"$f":"F!C72","v":"<1% or none, or largest pool occupies <0.01 hectares.  Enter \"1\" and SKIP to F20 (Floating Algae & Duckweed)."},{"$f":"F!D72","v":0},5,{"$f":"D37*E37","v":0}]
[null,null,{"$f":"F!C73","v":"1-5% of the ponded water.  Enter \"1\" and SKIP to F20."},{"$f":"F!D73","v":0},4,0]
[null,null,{"$f":"F!C74","v":"5-30% of the ponded water."},{"$f":"F!D74","v":0},3,0]
[null,null,{"$f":"F!C75","v":"30-70% of the ponded water."},{"$f":"F!D75","v":0},2,0]
[null,null,{"$f":"F!C76","v":"70-99% of the ponded water."},{"$f":"F!D76","v":0},1,0]
[null,null,{"$f":"F!C77","v":"100% of the ponded water. "},{"$f":"F!D77","v":0},0,0]
[{"$f":"F!A78","v":"F15"},{"$f":"F!B78","v":"Flat Shoreline Extent"},{"$f":"F!C78","v":"The length of the AA's shoreline (along its ponded open water) that is bordered by areas that are nearly flat (a slope less than about 5%) is:"},null,null,null,{"$f":"IF((AllSat+AllSat1>0),\"\",IF((OpenW=0),\"\", IF((SmallAA=1),\"\", MAX(F44:F48)/MAX(E44:E48))))","v":""},"WatEdgeSlope2","Wetlands whose shorelines have gentle slope are more likely than those with steep ones to retain sediment runoff from adjoining uplands, and are likely to have more vegetation that facilitates this. In calculations, is excluded automatically (cell goes blank) if wetland never has surface water during an average year. Also is excluded automatically if wetland lacks open water or is <0.01 ha."]
[null,null,{"$f":"F!C79","v":"<1%"},{"$f":"F!D79","v":0},0,{"$f":"D44*E44","v":0}]
[null,null,{"$f":"F!C80","v":"1-25%"},{"$f":"F!D80","v":0},1,{"$f":"D45*E45","v":0}]
[null,null,{"$f":"F!C81","v":"25-50%"},{"$f":"F!D81","v":0},2,{"$f":"D46*E46","v":0}]
[null,null,{"$f":"F!C82","v":"50-75%"},{"$f":"F!D82","v":0},3,{"$f":"D47*E47","v":0}]
[null,null,{"$f":"F!C83","v":">75%"},{"$f":"F!D83","v":0},4,{"$f":"D48*E48","v":0}]
[{"$f":"F!A84","v":"F16"},{"$f":"F!B84","v":"Predominant Width of Vegetated Zone within Wetland"},{"$f":"F!C84","v":"At the driest time of year (or lowest water level), the average width of vegetated area in the AA that separates adjoining uplands from open water within the AA is:"},null,null,null,{"$f":"IF((AllSat+AllSat1>0),\"\",IF((OpenW=0),\"\", IF((SmallAA=1),\"\", MAX(F50:F54)/MAX(E50:E54))))","v":""},"WidthAbs2","Wider vegetated areas provide more area for sediment particles borne in runoff to be filtered and deposited. Knutson et al. (1981) found that emergent wetlands wider than 30 feet reduced wave energy by 88% while those less than 6 feet wide were relatively ineffective in wave buffering. Many studies have shown that sediment retention is greatest in the first 5-20 ft of a buffer, that is, the most uphill portion, which is closest to potential inputs of runoff-borne sediment (Polyakov et al. 2005, White et al. 2007). However, this depends on steepness of the terrain, erodibility and infiltration capacity of the soil, ground cover, antecedent soil saturation, sediment particle size, and runoff intensity. Wider buffers are required when runoff carries finer-sized particles (e.g., clay).  In calculations, is excluded automatically (cell goes blank) if wetland never has surface water during an average year. Also is excluded automatically if wetland lacks open water or is <0.01 ha."]
[null,null,{"$f":"F!C85","v":"<1 m"},{"$f":"F!D85","v":0},0,{"$f":"D50*E50","v":0}]
[null,null,{"$f":"F!C86","v":"1 - 9 m"},{"$f":"F!D86","v":0},2,{"$f":"D51*E51","v":0}]
[null,null,{"$f":"F!C87","v":"10 - 29 m"},{"$f":"F!D87","v":0},3,{"$f":"D52*E52","v":0}]
[null,null,{"$f":"F!C88","v":"30 - 49 m"},{"$f":"F!D88","v":0},4,{"$f":"D53*E53","v":0}]
[null,null,{"$f":"F!C90","v":"> 100 m"},{"$f":"F!D90","v":0},5,{"$f":"D54*E54","v":0}]
[{"$f":"F!A95","v":"F18"},{"$f":"F!B95","v":"Interspersion of Robust Emergents & Open Water"},{"$f":"F!C95","v":"During most of the growing season, the spatial pattern of tall robust herbaceous vegetation (e.g., cattail, bulrush) that has surface water beneath it is mostly:"},null,null,null,{"$f":"IF((AllSat+AllSat1>0),\"\",IF((NoPonded=1),\"\",IF((NoOpenPonded+NoOpenPonded1>0),\"\",IF((AllOpenPond=1),\"\", IF((SmallAA=1),\"\", MAX(F56:F58)/MAX(E56:E58))))))","v":0},"Interspers2","Greater interspersion of open water and vegetation should allow more contact between plants and moving sediment-bearing water, resulting in greater deposition of suspended sediment. In calculations, is excluded automatically (cell goes blank) if wetland never has surface water during an average year, if no ponded water, if ponded water but no vegetation, or if ponded but no open water."]
[null,null,{"$f":"F!C96","v":"Scattered in small clumps, islands, or patches throughout the surface water area."},{"$f":"F!D96","v":0},2,{"$f":"D56*E56","v":0}]
[null,null,{"$f":"F!C97","v":"Intermediate"},{"$f":"F!D97","v":0},1,0]
[null,null,{"$f":"F!C98","v":"Clumped at one or a few sides of the surface water area, or mostly surrounds a central area of open water.  Or such vegetation is absent or covers <9 sq m and <1% of the AA."},{"$f":"F!D98","v":0},0,0]
[{"$f":"F!A109","v":"F25"},{"$f":"F!B109","v":"Through Flow Pattern"},{"$f":"F!C109","v":"During its travel through the AA at the time of peak annual flow, most of the water arriving in channels [select only the ONE encountered by most of the incoming water]:"},null,null,null,{"$f":"IF((AllSat=1),\"\",IF((Inflows=0),\"\",(MAX(F60:F64)/MAX(E60:E64))))","v":""},"ThruFlo2","Like a constricted outlet, vegetation and other obstacles create a \"roughness\" within a wetland that can slow the water and allow sediment particles to be deposited. This is much truer if the vegetation intercepts a large proportion of the flow during high-flow periods (i.e., is not merely along an upland edge that never floods). Although tall and stiff vegetation provides the most resistance and thus sedimentation, it often tends to have less ground cover, so the net effect is uncertain in some wetlands. Water takes longer to move through complex channel networks (e.g., braided or sinuous) which themselves provide additional friction, thus allowing more suspended sediment to be deposited. The sinuosity is as much the result of sedimentation-erosion dynamics as it is the cause of them. Wetlands with a sheet flow pattern often retain more suspended solids than channelized systems (Morris et al. 1981). In calculations, is excluded automatically (cell goes blank) if wetland never has surface water during an average year or if no surface inflows."]
[null,null,{"$f":"F!C110","v":"Does not bump into plant stems as it travels through the AA.  Nearly all the water continues to travel in unvegetated (often incised) channels that have little contact with wetland vegetation, or through a zone of open water such as an instream pond or lake."},{"$f":"F!D110","v":0},0,{"$f":"D60*E60","v":0}]
[null,null,{"$f":"F!C111","v":"bumps into herbaceous vegetation but mostly remains in fairly straight channels."},{"$f":"F!D111","v":0},3,{"$f":"D61*E61","v":0}]
[null,null,{"$f":"F!C112","v":"bumps into herbaceous vegetation and mostly spreads throughout, or is in widely  meandering, multi-branched, or braided channels."},{"$f":"F!D112","v":0},6,{"$f":"D62*E62","v":0}]
[null,null,{"$f":"F!C113","v":"bumps into tree trunks and/or shrub stems but mostly remains in fairly straight channels."},{"$f":"F!D113","v":0},4,{"$f":"D63*E63","v":0}]
[null,null,{"$f":"F!C114","v":"bumps into tree trunks and/or shrub stems and follows a fairly indirect path from entrance to exit (meandering, multi-branched, or braided)"},{"$f":"F!D114","v":0},8,{"$f":"D64*E64","v":0}]
[{"$f":"F!A115","v":"F26"},{"$f":"F!B115","v":"Channel Connection & Outflow Duration"},{"$f":"F!C115","v":"The most persistent surface water connection (outlet channel or pipe, ditch, or overbank water exchange) between the AA and the closest off-site downslope water body is:"},null,null,null,{"$f":"IF((AllSat+AllSat1>0),\"\", MAX(F66:F70)/MAX(E66:E70))","v":0},"OutDur2","Wetlands that lack outlets retain all sediment that enters them, and very little is remobilized and exported downgradient over the long term.  Wetlands that connect to downslope water bodies for only part of the year may export less sediment annually than those with persistent outflow. In calculations, is excluded automatically (cell goes blank) if wetland never has surface water during an average year."]
[null,null,{"$f":"F!C116","v":"persistent (>9 months/year, including times when frozen)"},{"$f":"F!D116","v":0},1,{"$f":"D66*E66","v":0}]
[null,null,{"$f":"F!C117","v":"seasonal (14 days to 9 months/year, not necessarily consecutive, including times when frozen)"},{"$f":"F!D117","v":0},2,{"$f":"D67*E67","v":0}]
[null,null,{"$f":"F!C118","v":"temporary (<14 days, not necessarily consecutive -- must be unfrozen)"},{"$f":"F!D118","v":0},4,{"$f":"D68*E68","v":0}]
[null,null,{"$f":"F!C119","v":"none -- but maps show a stream or other water body that is downslope from the AA and within a distance that is less than the AA's length.  If so, mark \"1\" here and SKIP TO F28 (Groundwater). "},{"$f":"F!D119","v":0},8,{"$f":"D69*E69","v":0}]
[null,null,{"$f":"F!C120","v":"no surface water flows out of the wetland except possibly during extreme events (<once per 10 years). Or, water flows only into a wetland, ditch, or lake that lacks an outlet.  If so, mark \"1\" here and SKIP TO F28 (Groundwater). "},{"$f":"F!D120","v":0},8,{"$f":"D70*E70","v":0}]
[{"$f":"F!A121","v":"F27"},{"$f":"F!B121","v":"Outflow Confinement"},{"$f":"F!C121","v":"During major runoff events, in the places where surface water exits the AA or connected waters nearby, it:"},null,null,null,{"$f":"IF((OutNone+OutNone1>0),\"\",MAX(F72:F74)/MAX(E72:E74))","v":0},"Constric2","Narrow outlets limit water outflow from a wetland and its downstream or downslope movement, thus causing water to back up into the wetland, which allows more time for suspended sediments to be deposited. The types of outlets described here are ones that typically are more constricted than natural channels. Natural channels usually have adjusted over time to local runoff and thus tend to be wider relative to volume of flow received. A restricting outlet in wetlands can reduce export of sediment (Amatya et al. 2003). In calculations, is excluded automatically (cell goes blank) if no outlet.  In calculations, is excluded automatically (cell goes blank) if wetland has no surface water outlet."]
[null,null,{"$f":"F!C122","v":"mostly passes through a pipe, culvert, narrowly breached dike, berm, beaver dam, or other partial obstruction (other than natural topography) that does not appear to drain the wetland artificially during most of the growing season."},{"$f":"F!D122","v":0},2,{"$f":"D72*E72","v":0}]
[null,null,{"$f":"F!C123","v":"leaves through natural exits (channels or diffuse outflow), not mainly through artificial or temporary features"},{"$f":"F!D123","v":0},1,{"$f":"D73*E73","v":0}]
[null,null,{"$f":"F!C124","v":"exported more quickly than usual due to ditches or pipes within the AA (or connected to its outlet or within 10 m of the AA's edge) which drain the wetland artificially, or water is pumped out of the AA."},{"$f":"F!D124","v":0},0,{"$f":"D74*E74","v":0}]
[{"$f":"F!A129","v":"F29"},{"$f":"F!B129","v":"Internal Gradient"},{"$f":"F!C129","v":"The gradient along most of the flow path within the AA is:"},null,null,null,{"$f":"MAX(F76:F79)/MAX(E76:E79)","v":0},"Gradient2","Flatter wetlands are more likely than steep ones to slow runoff, facilitating more deposition of suspended matter. Ground cover becomes more important to sediment stabilization in wetlands on slopes. A Pennsylvania study found that slope wetlands tended to have the lowest sediment accretion rates of any wetland type (HGM class) (Wardrop & Brooks 1998)."]
[null,null,{"$f":"F!C130","v":"<2%, or, no slope is ever apparent (i.e., flat). Or, the wetland is in a depression or pond with no inlet and no outlet."},{"$f":"F!D130","v":0},4,{"$f":"D76*E76","v":0}]
[null,null,{"$f":"F!C131","v":"2-5%"},{"$f":"F!D131","v":0},2,{"$f":"D77*E77","v":0}]
[null,null,{"$f":"F!C132","v":"6-10%"},{"$f":"F!D132","v":0},1,{"$f":"D78*E78","v":0}]
[null,null,{"$f":"F!C133","v":">10%"},{"$f":"F!D133","v":0},0,{"$f":"D79*E79","v":0}]
[{"$f":"F!A194","v":"F41"},{"$f":"F!B194","v":"% Bare Ground & Thatch"},{"$f":"F!C194","v":"Consider the parts of the AA that lack surface water at the driest time of the growing season.  Viewed from directly above the ground layer, the predominant condition in those areas at that time is:"},null,null,null,{"$f":"MAX(F81:F84)/MAX(E81:E84)","v":0},"Gcover2","Dense vegetation offers frictional resistance to water flow, promoting sedimentation of suspended particles, as well as reducing the resuspension of bottom sediments by waves and currents."]
[null,null,{"$f":"F!C195","v":"Little or no (<5%) bare ground is visible between erect stems or under canopy anywhere in the vegetated AA. Ground is extensively blanketed by dense thatch, moss, lichens, graminoids with great stem densities, or plants with ground-hugging foliage. "},{"$f":"F!D195","v":0},5,{"$f":"D81*E81","v":0}]
[null,null,{"$f":"F!C196","v":"Slightly bare ground (5-20% bare between plants) is visible in places, but those areas comprise less than 5% of the unflooded parts of the AA."},{"$f":"F!D196","v":0},4,{"$f":"D82*E82","v":0}]
[null,null,{"$f":"F!C197","v":"Much bare ground (20-50% bare between plants) is visible in places, and those areas comprise more than 5% of the unflooded parts of the AA. "},{"$f":"F!D197","v":0},2,{"$f":"D83*E83","v":0}]
[null,null,{"$f":"F!C198","v":"Other conditions"},{"$f":"F!D198","v":0},0,{"$f":"D84*E84","v":0}]
[{"$f":"F!A200","v":"F42"},{"$f":"F!B200","v":"Ground Irregularity"},{"$f":"F!C200","v":"Consider the parts of the AA that lack surface water at some time of the year.  Excluding slash from logging, the number of small pits, raised mounds, hummocks, boulders, upturned trees, animal burrows, gullies, natural levees, wide soil cracks, and microdepressions is:"},null,null,null,{"$f":"MAX(F86:F88)/MAX(E86:E88)","v":0},"Girreg2","These features cumulatively decelerate runoff, thus allowing for more sedimentation to occur, although usually only to a minor degree."]
[null,null,{"$f":"F!C201","v":"Few or none (minimal microtopography; <1% of that area) "},{"$f":"F!D201","v":0},0,{"$f":"D86*E86","v":0}]
[null,null,{"$f":"F!C202","v":"Intermediate"},{"$f":"F!D202","v":0},1,{"$f":"D87*E87","v":0}]
[null,null,{"$f":"F!C203","v":"Several (extensive micro-topography)"},{"$f":"F!D203","v":0},2,{"$f":"D88*E88","v":0}]
[{"$f":"F!A323","v":"F68"},{"$f":"F!B323","v":"Wetland as a % of Its Contributing Area (Catchment)"},{"$f":"F!C323","v":"View the approximate boundaries of the wetland's catchment (CA) as shown in the map AESRD provides in response to your data request.  Then adjust those boundaries if necessary based on your field observations of the surrounding terrain, and/or by using procedures described in the ABWRET Manual. Relative to the extent of this catchment (but excluding the area of the AA), this AA and any bordering waters together comprise (select ONE):"},null,null,null,{"$f":"MAX(F90:F93)/MAX(E90:E93)","v":0},"WetPctCA2","Sediment deposition can be predicted largely by the ratio of the volume of a storage basin to the volume of runoff entering the basin (Heinemann 1981)."]
[null,null,{"$f":"F!C324","v":"<1% of their catchment"},{"$f":"F!D324","v":0},0,{"$f":"D90*E90","v":0}]
[null,null,{"$f":"F!C325","v":"1 to 10% of their catchment"},{"$f":"F!D325","v":0},1,0]
[null,null,{"$f":"F!C326","v":"10 to 100%  of their catchment"},{"$f":"F!D326","v":0},2,0]
[null,null,{"$f":"F!C327","v":"Larger than the area of their catchment (wetland has essentially no catchment, e.g., isolated by dikes with no input channels, or is a raised bog). "},{"$f":"F!D327","v":0},3,0]
[{"$f":"S!A64","v":"S9"},{"$f":"S!B64","v":"Soil or Sediment Alteration Within the Assessment Area"},null,{"$f":"S!F81","v":0},null,null,{"$f":"1-D94","v":1},"SoilAlt2","If soils within a wetland are being disturbed or eroded, it is less likely the wetland will retain sediment on a net annual basis."]
[]
[null,null,"Entrainment and Storage [TRAP]"]
[null,"Wetlands <10 hectares:","[ AVERAGE(WetVegArea, OpenPonded2, Interspers2) + AVERAGE(Sub0Days, SlopeBuffer, Gradient2) + AVERAGE (WetPctCA2,SeasPct2, Fluc2, DepthC2, WatEdgeSlope2, WidthAbs2, Iso2,ThruFlo2, Constric2, Gcover2, Girreg2,  SoilAlt2) ] / 3",null,null,null,{"$f":"IF((GT10HA=1),G98, IFERROR((AVERAGE(WetVegArea, OpenPonded2, Interspers2) + AVERAGE(Sub0Days, SlopeBuffer, Gradient2) + AVERAGE(WetPctCA2,SeasPct2, Fluc2, DepthC2, WatEdgeSlope2, WidthAbs2, ISN2,  ThruFlo2, Constric2, Gcover2, Girreg2,  SoilAlt2)) / 3,\"\"))","v":4.1666666666666664E-2}]
[null,"Wetlands >10 hectares:","Substituted 1-OWpct, MixWaterVeg and added LGindex.",null,null,null,{"$f":"IFERROR((AVERAGE(WetVegArea, 1-OWpct, MixWaterVeg) + AVERAGE(1-Sub0Days, SlopeBuffer, LGIndex,Gradient2) + AVERAGE(WetPctCA2,SeasPct2, Fluc2, DepthC2, WatEdgeSlope2, WidthAbs2, ISN4, ThruFlo2, Constric2, Gcover2, Girreg2,  SoilAlt2)) / 3,\"\")","v":0.54166666666666663}]
[]
[null,null,"Export [OUT]"]
[null,null,"OutDur2",null,null,null,{"$f":"OutDur2","v":0}]
[]
[null,null,"ABWRET-A FUNCTION MODEL"]
[null,null,"Sediment Retention"]
[null,null,"IF((OutNone + OutNone1>0),10, ELSE: AVERAGE(TRAP, OUT)",null,null,null,{"$f":"IF((OutNone + OutNone1>0),10, 10*AVERAGE(TRAP1A, OUT2A))","v":0.20833333333333331}]
[null,null,null,null,null,null,null,null,"Literature Cited"]
[null,null,"ABWRET-E model:",null,null,null,null,null,"Alberti, M., D. Booth, K. Hill, B. Coburn, C. Avolio, S. Coe, and D. Spirandelli. 2007. The impact of urban patterns on aquatic ecosystems: An empirical analysis in Puget Lowland sub-basins. Landscape and Urban Planning 80:345-361."]
[null,1,"IF(ChannConn + RipFloodPl = 0), then =10",{"$f":"IF((ChannConn+RipFloodpl=0), 10, \"\")","v":10},null,null,null,null,"Amatya, D. M., R. W. Skaggs, J. W. Gilliam, and J. H. Hughes. 2003. Effects of orifice-weir outlet on hydrology and water quality of a drained forested watershed. Southern Journal of Applied Forestry 27:130-142."]
[null,2,"ELSE:",null,null,null,null,null,"Dillaha, T. A., J. H. Sherrard, D. Lee, S. Mostaghimi, and V. O. Shanholtz. 1988. Evaluation of vegetative filter strips as a best management practice for feed lots. Journal Water Pollution Control Federation 60:1231-1238."]
[null,null,"10*AVERAGE[ WetVegArea, 1-OWpct, MixWaterVeg, AVERAGE(1-Sub0Days, SlopeBuffer, LGindex) ]",{"$f":"IF((D108=10), 10, 10*AVERAGE(WetVegArea, 1-OWpct, MixWaterVeg, AVERAGE(1-Sub0Days, SlopeBuffer, LGIndex)))","v":10},null,null,null,null,"Dillaha, T. A., R. B. Reneau, S. Mostaghimi, and D. Lee. 1989. Vegetative filter strips for agricultural nonpoint source pollution-control. Transactions of the  ASAE 32:513-519."]
[null,null,null,null,null,null,null,null,"Evans, R. D. and F. H. Rigler. 1983. A test of lead-210 dating for the measurement of whole lake soft sediment accumulation. Canadian Journal of Fisheries and Aquatic Sciences 40:506-515."]
[null,null,"ABWRET-E with substitutions:",null,null,null,null,null,"Heinemann, H. G. 1981. A new sediment trap efficency curve for small reservoirs Water Resources Bulletin 17:825-830."]
[null,1,"IF(OutNone+OutNone1>0), then =10",{"$f":"IF((OutNone+OutNone1>0), 10, \"\")","v":""},null,null,null,null,"Knutson, P., J. Ford, M. Inskeep, and J. Oyler. 1981. National survey of planted salt marshes (Vegetative stabilization and wave stress). Wetlands 1:129-157."]
[null,2,"ELSE:",null,null,null,null,null,"McBride, M. and D. B. Booth. 2005. Urban impacts on physical stream condition: Effects of spatial scale, connectivity, and longitudinal trends. Journal of the American Water Resources Association 41:565-580."]
[null,null,"10*AVERAGE[ WetVegArea, OpenPonded2, Interspers2, AVERAGE(1-Sub0Days, SlopeBuffer, LGindex) ]",{"$f":"IF((D113=10),10, 10*AVERAGE(WetVegArea,OpenPonded2,Interspers2,AVERAGE(1-Sub0Days,SlopeBuffer,LGIndex)))","v":3.333333333333333},null,null,null,null,"Morris, A. W., A. J. Bale, and R. J. M. Howland. 1981. Nutrient distributions in an estuary - evidence of chemical precipitation of dissolved silicate and phosphate. Estuarine Coastal and Shelf Science 12:205-216."]
[null,null,null,null,null,null,null,null,"Nieswand, G. H., R. M. Hordon, T. B. Shelton, B. B. Chavooshian, and S. Blarr. 1990. Buffer strips to protect water-supply reservoirs - A model and recommendations. Water Resources Bulletin 26:959-966."]
[null,null,null,null,null,null,null,null,"Nolan, K. M. and D. C. Marron. 1985. Contrast in stream-channel response to major storms in two mountainous areas of California. Geology 13:135-138."]
[null,null,null,null,null,null,null,null,"Phillips, J. D. 1989. An evaluation of the factors determining the effectiveness of water quality buffer zones. Journal of Hydrology 107:133-145."]
[null,null,null,null,null,null,null,null,"Polyakov, V., A. Fares, and M. H. Ryder. 2005. Precision riparian buffers for the control of nonpoint source pollutant loading into surface water: A review. Environmental Reviews 13:129-144."]
[null,null,null,null,null,null,null,null,"Trimble, G. R., Jr. and R. S. Sartz. 1957. How far from a stream should a logging road be located? Journal of Forestry 55:339-341."]
[null,null,null,null,null,null,null,null,"Wardrop, D. H. and R. P. Brooks. 1998. The occurrence and impact of sedimentation in central Pennsylvania wetlands. Environmental Monitoring and Assessment 51:119-130."]
[null,null,null,null,null,null,null,null,"White, W. J., L. A. Morris, D. B. Warnell, A. P. Pinho, C. R. Jackson, and L. T. West. 2007. Sediment retention by forested filter strips in the Piedmont of Georgia. Journal of Soil and Water Conservation 62:453-463."]
[null,null,null,null,null,null,null,null,"Zhang, X., X. Liu, M. Zhang, R. A. Dahlgren, and M. Eitzel. 2010. A review of vegetated buffers and a meta-analysis of their mitigation efficacy in reducing nonpoint source pollution. Journal of Environmental Quality 39:76-84."]

{"sheet":"PR","index":13,"n_rows":140,"n_cols":9,"rows_kept":140,"cut":false,"hidden":false,"merged":[[0,0,0,1],[62,0,67,0],[62,1,67,1],[56,1,61,1],[12,0,18,0],[19,1,25,1],[27,1,31,1],[19,0,25,0],[27,0,31,0],[38,0,44,0],[38,1,44,1],[51,0,54,0],[51,1,54,1],[45,0,50,0],[45,1,50,1],[91,8,95,8],[86,8,90,8],[56,8,61,8],[82,0,85,0],[86,1,90,1],[91,0,95,0],[72,0,76,0],[72,1,76,1],[68,8,71,8],[62,8,67,8],[72,8,76,8],[77,8,81,8],[82,1,85,1],[77,1,81,1],[82,8,85,8],[68,0,71,0],[45,8,50,8],[45,7,50,7],[38,7,44,7],[51,7,54,7],[51,8,54,8],[38,8,44,8],[96,1,100,1],[96,8,100,8],[27,8,31,8],[96,0,100,0],[12,1,18,1],[32,0,37,0],[96,7,100,7],[12,7,18,7],[19,7,25,7],[27,7,31,7],[32,7,37,7],[12,8,18,8],[19,8,25,8],[32,1,37,1],[32,8,37,8],[91,7,95,7],[68,1,71,1],[56,0,61,0],[91,1,95,1],[86,0,90,0],[77,0,81,0],[0,4,0,7],[82,7,85,7],[86,7,90,7],[56,7,61,7],[62,7,67,7],[68,7,71,7],[72,7,76,7],[77,7,81,7]]}
["Phosphorus Retention",null,"The effectiveness for retaining phosphorus for long periods (>1 growing season) as a result of chemical adsorption, or from translocation by plants to belowground zones with less potential for physically or chemically remobilizing phosphorus into the water column.","PR",null,null,null,null,"The model does not address the ecological need for keeping phosphorus out of the surface or ground water at a particular location, as would be implied partly by the occurrence of nuisance blooms of algae or decline of plants that are sensitive to phosphorus overenrichment, at that location or downgradient.  "]
["#","Function Indicators from Estimator","Scoring Notes",null,null,null,"Normalised Score","Indicator Abbreviation      or Formula","Rationale"]
[{"$f":"OF!A5","v":"OF4"},{"$f":"OF!C5","v":"Channel Connection"},null,null,null,null,{"$f":"IF((ChannConn=\"\"),\"\",ChannConn)","v":""},"ChannConn","Wetlands that lack an outlet (never have any outflow) store all phosphorus that enters them."]
[{"$f":"OF!A23","v":"OF22"},{"$f":"OF!C23","v":"L/G Index (Residence Time)"},null,null,null,null,{"$f":"IF((LGIndex=\"\"),\"\",LGIndex)","v":""},"LGIndex","Phosphorus retention often correlates with detention time, which in turn correlates with flow path length within a wetland."]
[{"$f":"OF!A28","v":"OF27"},{"$f":"OF!C28","v":"Interspersion Index for Internal Water & Vegetation (macroscale)"},null,null,null,null,{"$f":"IF((MixWaterVeg=\"\"),\"\",MixWaterVeg)","v":""},"MixWaterVeg","Less clumping (more interspersion) of vegetation with open water is likely to support more phosphorus retention because it implies  more contact between plants that retain P and the P-bearing water."]
[{"$f":"OF!A31","v":"OF30"},{"$f":"OF!C31","v":"% of AA that is Open Water (macro scale)"},"Inverse",null,null,null,{"$f":"IF((OWpct=\"\"),\"\",1-OWpct)","v":""},"OWpct","Open water areas are more prone to wind that can mix of bottom sediments, resuspending the P-bearing sediment and resulting in export if an outlet is present. When there is proportionally more vegetation than open water, that provides potential for trapping suspended sediment and retaining its associated P."]
[{"$f":"OF!A47","v":"OF46"},{"$f":"OF!C47","v":"Organic Soil Content (macroscale)"},null,null,null,null,{"$f":"IF((SoilOrgPct=\"\"),\"\",SoilOrgPct)","v":""},"SoilOrgPct","Retention of phosphorus in boreal Alberta is correlated with the extent of rich fens, which are wetlands with greater soil organic matter than marshes and swamps (Prepas et al. 2011). "]
[{"$f":"OF!A49","v":"OF48"},{"$f":"OF!C49","v":"Soil Texture (macroscale)"},"See Table 2 worksheet.",null,null,null,{"$f":"IF((SoilTex_PR=\"\"),\"\",SoilTex_PR)","v":""},"SoilTex_PR","See above."]
[{"$f":"OF!A52","v":"OF51"},{"$f":"OF!C52","v":"Subzero Days"},"Inverse",null,null,null,{"$f":"IF((Sub0Days=\"\"),\"\",1-Sub0Days)","v":""},"Sub0Days","Wetlands frozen later into the spring are less able to retain P-bearing sediment suspended in snowmelt runoff.  "]
[{"$f":"OF!A61","v":"OF60"},{"$f":"OF!C61","v":"Water Permanence Probability"},"Inverse",null,null,null,{"$f":"IF((WatProb=\"\"),\"\",1-WatProb)","v":""},"WatProb","Sediments that remain covered with water year-round (and longer) tend to become anaerobic and release phosphorus, especially in deeper wetlands. Thus, wetlands with the lowest probability of having permanent water may be most retentive of whatever P they receive."]
[{"$f":"OF!A69","v":"OF68"},{"$f":"OF!C69","v":"Wetland Vegetated Area"},null,null,null,null,{"$f":"IF((WetVegArea=\"\"),\"\",WetVegArea)","v":""},"WetVegArea","Larger vegetated areas imply longer retention times that presumably promote greater P retention per unit area.  "]
["#","Function Indicators from Onsite Visit","Categorical Choices","Data","Weight","Data  x  Weight","Normalised Score","Indicator Abbreviation       or Formula","Rationale & Scoring Notes"]
[{"$f":"F!A17","v":"F3"},{"$f":"F!B17","v":"% Saturated Only"},{"$f":"F!C17","v":"The percentage of the AA that never contains surface water during an average year (that is, except perhaps for a few hours after snowmelt or rainstorms), but which is still a wetland, is:"},null,null,null,{"$f":"MAX(F14:F19)/MAX(E14:E19)","v":0},"SatPct3","Sites that remain continually moist (saturated) but not flooded may be more likely to retain phosphorus (Aldous et al. 2007). "]
[null,null,{"$f":"F!C18","v":"less than 1%, or <0.01 hectare (about 10 m on a side) never has surface water.  In other words, all or nearly all of the AA is inundated permanently or at least seasonally."},{"$f":"F!D18","v":0},0,{"$f":"D14*E14","v":0}]
[null,null,{"$f":"F!C19","v":"1-25% of the AA never contains surface water."},{"$f":"F!D19","v":0},1,0]
[null,null,{"$f":"F!C20","v":"25-50% of the AA never contains surface water."},{"$f":"F!D20","v":0},2,0]
[null,null,{"$f":"F!C21","v":"50-99% of the AA never contains surface water."},{"$f":"F!D21","v":0},3,0]
[null,null,{"$f":"F!C22","v":">99% of the AA never contains surface water, except for water flowing in channels and/or in pools that occupy <1% of the AA. SKIP to F26 (Channel Connection & Outflow Duration)"},{"$f":"F!D22","v":0},4,0]
[null,null,{"$f":"F!C23","v":">99% of the AA never contains surface water, and AA is not intersected by channels that have flow, not even for a few days per year. SKIP to F26."},{"$f":"F!D23","v":0},5,0]
[{"$f":"F!A24","v":"F4"},{"$f":"F!B24","v":"% with Persistent Surface Water"},{"$f":"F!C24","v":"The percentage of the AA that has surface water (either ponded or flowing, either open or obscured by vegetation) during all of the growing season during most years is:"},null,null,null,{"$f":"IF((AllSat+AllSat1>0),\"\",MAX(F21:F26)/MAX(E21:E26))","v":0},"Persis3","In some cases, sediments that remain covered with water year-round (and longer) tend to become anaerobic and release phosphorus, especially in deeper wetlands. Thus, wetlands with the least extent of persistent water may be most retentive of whatever P they receive.  In contrast, seasonal drawdowns can mobilize phosphorus that has accumulated in sediments (Snyder & Morace 1997, Aldous et al. 2005). To a perhaps lesser extent, reflooding of soils that have been dry for extended periods also can mobilize phosphorus, especially if flooding creates anoxic conditions (Burley et al. 2001), or if large quantities of leaf litter and other organic matter are present and rapidly decompose or leach phosphorus. In calculations, is excluded automatically (cell goes blank) if wetland never has surface water during an average year."]
[null,null,{"$f":"F!C25","v":"less than 1%, or <0.01 hectare (whichever is less).  SKIP to F8 (% Flooded Only Seasonally)."},{"$f":"F!D25","v":0},5,{"$f":"D21*E21","v":0}]
[null,null,{"$f":"F!C26","v":"1-25% of the AA, and mostly in narrow channels and/or small scattered pools."},{"$f":"F!D26","v":0},4,0]
[null,null,{"$f":"F!C27","v":"1-25% of the AA, and mostly in a single large pool, pond, and/or channel."},{"$f":"F!D27","v":0},4,0]
[null,null,{"$f":"F!C28","v":"25-50% of the AA"},{"$f":"F!D28","v":0},3,0]
[null,null,{"$f":"F!C29","v":"50-95% of the AA"},{"$f":"F!D29","v":0},2,0]
[null,null,{"$f":"F!C30","v":">95% of the AA"},{"$f":"F!D30","v":0},1,0]
[{"$f":"F!A38","v":"F7"},{"$f":"F!B38","v":"Lacustrine Wetland"},{"$f":"F!C38","v":"The AA borders a body of ponded open water whose size -- not counting the vegetated AA -- exceeds 8 hectares (about 300 x 300 m) during most of the growing season.  Enter \"1\" if true, \"0\" if false."},{"$f":"F!D38","v":0},null,null,{"$f":"IF((AllSat+AllSat1>D302),\"\",IF((NoPersis=1),\"\",D27))","v":0},"Lake3","Lacustrine wetlands are more likely than bogs or fens to be phosphorus-limited (Walbridge & Navaratnam 2006), and thus should be more able to take up and retain phosphorus. In calculations, is excluded automatically (cell goes blank) if wetland never has surface water during an average year."]
[{"$f":"F!A45","v":"F9"},{"$f":"F!B45","v":"Annual Water Fluctuation Range"},{"$f":"F!C45","v":"The annual fluctuation in surface water level within most of the parts of the AA that contain surface water is:"},null,null,null,{"$f":"IF((AllSat+AllSat1>0),\"\",IF((NoSeasonal=1),\"\",MAX(F29:F32)/MAX(E29:E32)))","v":0},"Fluctu3","Wetting and drying of sediments, as happens especially in wetlands with large water level fluctuations, increases the leaching and desorption of phosphorus from sediment organic matter, thus resulting in net export. However, stable water levels also can promote phosphorus export (not retention) because they are often associated with anoxic conditions that result in increased mobility of phosphorus. Sediment P release and subsequent export is particularly strong during periods of seasonal anoxia (Burley et al. 2001). In calculations, is excluded automatically (cell goes blank) if wetland never has surface water during an average year, or if none of it floods only seasonally."]
[null,null,{"$f":"F!C46","v":"<10 cm change (stable) "},{"$f":"F!D46","v":0},5,{"$f":"D29*E29","v":0}]
[null,null,{"$f":"F!C47","v":"10 cm - 50 cm change"},{"$f":"F!D47","v":0},3,{"$f":"D30*E30","v":0}]
[null,null,{"$f":"F!C49","v":"1-2 m change"},{"$f":"F!D49","v":0},2,{"$f":"D31*E31","v":0}]
[null,null,{"$f":"F!C50","v":">2 m change"},{"$f":"F!D50","v":0},1,{"$f":"D32*E32","v":0}]
[{"$f":"F!A52","v":"F10"},{"$f":"F!B52","v":"Predominant Depth Class"},{"$f":"F!C52","v":"During most of the time when water is present, its depth in most of the area is: [Note: This is not asking for the maximum depth.]"},null,null,null,{"$f":"IF((AllSat+AllSat1>0),\"\", IF((SmallAA=1),\"\", MAX(F34:F38)/MAX(E34:E38)))","v":0},"DomDepth3","Deeper wetlands are more likely to experience anoxic conditions that promote P mobility and export. However, deeper waters also imply slower water velocity, longer water detention time, more time for biological processing of phosphorus, and reduced likelihood of phosphorus associated with deposited sediments being resuspended by wind mixing or currents. In calculations, is excluded automatically (cell goes blank) if wetland never has surface water during an average year, or if wetland is <0.01 ha.."]
[null,null,{"$f":"F!C53","v":"<10 cm deep (but >0)"},{"$f":"F!D53","v":0},1,{"$f":"D34*E34","v":0}]
[null,null,{"$f":"F!C54","v":"10 - 50 cm deep"},{"$f":"F!D54","v":0},2,{"$f":"D35*E35","v":0}]
[null,null,{"$f":"F!C55","v":"0.5 - 1 m deep"},{"$f":"F!D55","v":0},5,{"$f":"D36*E36","v":0}]
[null,null,{"$f":"F!C56","v":"1 - 2 m deep"},{"$f":"F!D56","v":0},4,{"$f":"D37*E37","v":0}]
[null,null,{"$f":"F!C57","v":">2 m deep.  True for many fringe wetlands."},{"$f":"F!D57","v":0},3,{"$f":"D38*E38","v":0}]
[{"$f":"F!A71","v":"F14"},{"$f":"F!B71","v":"% of Ponded Water That Is Open "},{"$f":"F!C71","v":"In ducks-eye aerial view, the percentage of the ponded water that is open (lacking emergent vegetation during most of the growing season, and unhidden by a forest or shrub canopy) is:"},null,null,null,{"$f":"IF((AllSat+AllSat1>0),\"\",IF((NoPonded=1),\"\", IF((SmallAA=1),\"\", MAX(F40:F45)/MAX(E40:E45))))","v":0},"OpenWpct3","Plants take up phosphorus from sediments (and some, from the water directly) and can facilitate long-term retention if P is transferred to roots that are not as subject as the foliage is to leaching the nutrients back into the water column. Plants also facilitate sediment deposition by slowing the water, and much phosphorus is adsorbed on that sediment so is also deposited and potentially retained.  However, their decaying foliage also frequently creates anoxic conditions that promote P release from sediments, if iron concentrations are low and aeration by currents and wind is poor (as tends to occur when emergent and submersed aquatic plants occupy most of a water body). In calculations, is excluded automatically (cell goes blank) if wetland never has surface water during an average year. Also is excluded automatically if wetland has no ponded water or is <0.01 ha."]
[null,null,{"$f":"F!C72","v":"<1% or none, or largest pool occupies <0.01 hectares.  Enter \"1\" and SKIP to F20 (Floating Algae & Duckweed)."},{"$f":"F!D72","v":0},5,{"$f":"D40*E40","v":0}]
[null,null,{"$f":"F!C73","v":"1-5% of the ponded water.  Enter \"1\" and SKIP to F20."},{"$f":"F!D73","v":0},4,0]
[null,null,{"$f":"F!C74","v":"5-30% of the ponded water."},{"$f":"F!D74","v":0},3,0]
[null,null,{"$f":"F!C75","v":"30-70% of the ponded water."},{"$f":"F!D75","v":0},2,0]
[null,null,{"$f":"F!C76","v":"70-99% of the ponded water."},{"$f":"F!D76","v":0},1,0]
[null,null,{"$f":"F!C77","v":"100% of the ponded water. "},{"$f":"F!D77","v":0},0,0]
[{"$f":"F!A84","v":"F16"},{"$f":"F!B84","v":"Predominant Width of Vegetated Zone within Wetland"},{"$f":"F!C84","v":"At the driest time of year (or lowest water level), the average width of vegetated area in the AA that separates adjoining uplands from open water within the AA is:"},null,null,null,{"$f":"IF((AllSat+AllSat1>0),\"\",IF((OpenW=0),\"\",IF((SmallAA=1),\"\", MAX(F47:F51)/MAX(E47:E51))))","v":""},"VegWabs3","Wider vegetated areas provide more area for phosphorus adsorbed to sediment particles in runoff to be filtered and deposited. Where phosphorus is mainly attached to sediment (as often it is), then buffer widths sufficient for sediment retention (generally 10-30 ft) may be almost as effective for retaining phosphorus (White et al. 2007). But if phosphorus is mostly in dissolved form (orthophosphate, or soluble reactive phosphorus), then vegetated buffers may need to be very large or may not be effective at all (Prepas et al. 2001, Hoffman et al. 2009). In calculations, is excluded automatically (cell goes blank) if wetland never has surface water during an average year, or no open water, or if wetland is <0.01 ha.."]
[null,null,{"$f":"F!C85","v":"<1 m"},{"$f":"F!D85","v":0},0,{"$f":"D47*E47","v":0}]
[null,null,{"$f":"F!C86","v":"1 - 9 m"},{"$f":"F!D86","v":0},2,{"$f":"D48*E48","v":0}]
[null,null,{"$f":"F!C87","v":"10 - 29 m"},{"$f":"F!D87","v":0},3,{"$f":"D49*E49","v":0}]
[null,null,{"$f":"F!C88","v":"30 - 49 m"},{"$f":"F!D88","v":0},4,{"$f":"D50*E50","v":0}]
[null,null,{"$f":"F!C90","v":"> 100 m"},{"$f":"F!D90","v":0},5,{"$f":"D51*E51","v":0}]
[{"$f":"F!A95","v":"F18"},{"$f":"F!B95","v":"Interspersion of Robust Emergents & Open Water"},{"$f":"F!C95","v":"During most of the growing season, the spatial pattern of tall robust herbaceous vegetation (e.g., cattail, bulrush) that has surface water beneath it is mostly:"},null,null,null,{"$f":"IF((AllSat+AllSat1>0),\"\",IF((NoPonded=1),\"\", IF((NoOpenPonded+ NoOpenPonded1>0),\"\", IF((AllOpenPond=1),\"\", IF((SmallAA=1),\"\", MAX(F53:F55)/MAX(E53:E55))))))","v":0},"Interspers3","Greater interspersion of open water and vegetation is hypothesized to support greater sediment and phosphorus removal. That is because plants assist the deposition of suspended sediment which contains P, while open water areas tend to be more aerobic which immobilizes P in the deposited sediment. In calculations, is excluded automatically (cell goes blank) if wetland never has surface water during an average year, if no ponded water, if ponded water but no vegetation, or if ponded but no open water."]
[null,null,{"$f":"F!C96","v":"Scattered in small clumps, islands, or patches throughout the surface water area."},{"$f":"F!D96","v":0},2,{"$f":"D53*E53","v":0}]
[null,null,{"$f":"F!C97","v":"Intermediate"},{"$f":"F!D97","v":0},1,{"$f":"D54*E54","v":0}]
[null,null,{"$f":"F!C98","v":"Clumped at one or a few sides of the surface water area, or mostly surrounds a central area of open water.  Or such vegetation is absent or covers <9 sq m and <1% of the AA."},{"$f":"F!D98","v":0},0,{"$f":"D55*E55","v":0}]
[{"$f":"F!A100","v":"F20"},{"$f":"F!B100","v":"Floating Algae & Duckweed"},{"$f":"F!C100","v":"At some time of the year, mats of algae and/or duckweed cover most of the AA's otherwise-unshaded water surface or blanket the underwater substrate.  If true, enter \"1\" in next column.  If untrue or uncertain, enter \"0\"."},{"$f":"F!D100","v":0},null,null,{"$f":"IF((AllSat+AllSat1>0),\"\", IF((NoPonded=1),\"\", IF((SmallAA=1),\"\", IF((D56=1),0,\"\"))))","v":""},"Algae3","A proliferation of algae and floating aquatics can indicate that the wetland is receiving more nutrients than it is capable of processing effectively.  These non-rooted plants do not oxygenate the sediments, they take up and store nutrients only briefly, and their die-offs create anoxic conditions that mobilize phosphorus temporarily retained in sediments. In the calculations, abundant algae reduces the score but absence of blooms does not increase it. In calculations, is excluded automatically (cell goes blank) if wetland never has surface water during an average year, or if wetland is <0.01 ha."]
[{"$f":"F!A109","v":"F25"},{"$f":"F!B109","v":"Through Flow Pattern"},{"$f":"F!C109","v":"During its travel through the AA at the time of peak annual flow, most of the water arriving in channels [select only the ONE encountered by most of the incoming water]:"},null,null,null,{"$f":"IF((AllSat=1),\"\", IF((Inflows=0),\"\",MAX(F58:F62)/MAX(E58:E62)))","v":""},"ThruFlo3","Like a constricted outlet, vegetation and other obstacles create a \"roughness\" within a wetland that can slow the water and allow phosphorus adsorbed to sediment particles to be deposited. This is much truer if the vegetation intercepts a large proportion of the flow during high-flow periods (i.e., is not merely along an upland edge that never floods). Although tall and stiff vegetation provides the most resistance and thus may be more effective at allowing sediment to be deposited, it often tends to have less ground cover, so the net effect is uncertain in some wetlands. Water takes longer to move through complex channel networks (e.g., braided or sinuous) which themselves provide additional friction, thus allowing more suspended sediment and the phosphorus associated with it to be deposited. Wetlands with a sheet flow pattern often retain more total phosphorus than channelized systems (Morris et al. 1981, Knox et al. 2008). In calculations, is excluded automatically (cell goes blank) if wetland never has surface water during an average year or if no surface inflows."]
[null,null,{"$f":"F!C110","v":"Does not bump into plant stems as it travels through the AA.  Nearly all the water continues to travel in unvegetated (often incised) channels that have little contact with wetland vegetation, or through a zone of open water such as an instream pond or lake."},{"$f":"F!D110","v":0},0,{"$f":"D58*E58","v":0}]
[null,null,{"$f":"F!C111","v":"bumps into herbaceous vegetation but mostly remains in fairly straight channels."},{"$f":"F!D111","v":0},1,{"$f":"D59*E59","v":0}]
[null,null,{"$f":"F!C112","v":"bumps into herbaceous vegetation and mostly spreads throughout, or is in widely  meandering, multi-branched, or braided channels."},{"$f":"F!D112","v":0},2,{"$f":"D60*E60","v":0}]
[null,null,{"$f":"F!C113","v":"bumps into tree trunks and/or shrub stems but mostly remains in fairly straight channels."},{"$f":"F!D113","v":0},3,{"$f":"D61*E61","v":0}]
[null,null,{"$f":"F!C114","v":"bumps into tree trunks and/or shrub stems and follows a fairly indirect path from entrance to exit (meandering, multi-branched, or braided)"},{"$f":"F!D114","v":0},4,{"$f":"D62*E62","v":0}]
[{"$f":"F!A115","v":"F26"},{"$f":"F!B115","v":"Channel Connection & Outflow Duration"},{"$f":"F!C115","v":"The most persistent surface water connection (outlet channel or pipe, ditch, or overbank water exchange) between the AA and the closest off-site downslope water body is:"},null,null,null,{"$f":"IF((AllSat+AllSat1>0),\"\",(MAX(F64:F68))/MAX(E64:E68))","v":0},"OutDura3","Wetlands that lack outlets retain all phosphorus that enters them. Wetlands that connect to downslope water bodies for only part of the year may export less phosphorus annually than those with persistent outflow. In calculations, is excluded automatically (cell goes blank) if wetland never has surface water during an average year."]
[null,null,{"$f":"F!C116","v":"persistent (>9 months/year, including times when frozen)"},{"$f":"F!D116","v":0},1,{"$f":"D64*E64","v":0}]
[null,null,{"$f":"F!C117","v":"seasonal (14 days to 9 months/year, not necessarily consecutive, including times when frozen)"},{"$f":"F!D117","v":0},2,{"$f":"D65*E65","v":0}]
[null,null,{"$f":"F!C118","v":"temporary (<14 days, not necessarily consecutive -- must be unfrozen)"},{"$f":"F!D118","v":0},3,{"$f":"D66*E66","v":0}]
[null,null,{"$f":"F!C119","v":"none -- but maps show a stream or other water body that is downslope from the AA and within a distance that is less than the AA's length.  If so, mark \"1\" here and SKIP TO F28 (Groundwater). "},{"$f":"F!D119","v":0},6,{"$f":"D67*E67","v":0}]
[null,null,{"$f":"F!C120","v":"no surface water flows out of the wetland except possibly during extreme events (<once per 10 years). Or, water flows only into a wetland, ditch, or lake that lacks an outlet.  If so, mark \"1\" here and SKIP TO F28 (Groundwater). "},{"$f":"F!D120","v":0},6,{"$f":"D68*E68","v":0}]
[{"$f":"F!A121","v":"F27"},{"$f":"F!B121","v":"Outflow Confinement"},{"$f":"F!C121","v":"During major runoff events, in the places where surface water exits the AA or connected waters nearby, it:"},null,null,null,{"$f":"IF((OutNone + OutNone1>0),\"\",(MAX(F70:F72)/MAX(E70:E72)))","v":0},"Constric3","Narrow outlets limit water outflow from a wetland and its downstream or downslope movement, thus causing water to back up into the wetland, which allows more time for sediments to be deposited and phosphorus to be processed. The types of outlets described here are ones that typically are more constricted than natural channels, which usually have adjusted over time to local runoff and thus are wider relative to volume of flow received. A restricting outlet in wetlands can reduce export of phosphorus (Amatya et al. 2003). In calculations, is excluded automatically (cell goes blank) if no outlet."]
[null,null,{"$f":"F!C122","v":"mostly passes through a pipe, culvert, narrowly breached dike, berm, beaver dam, or other partial obstruction (other than natural topography) that does not appear to drain the wetland artificially during most of the growing season."},{"$f":"F!D122","v":0},1,{"$f":"D70*E70","v":0}]
[null,null,{"$f":"F!C123","v":"leaves through natural exits (channels or diffuse outflow), not mainly through artificial or temporary features"},{"$f":"F!D123","v":0},0,{"$f":"D71*E71","v":0}]
[null,null,{"$f":"F!C124","v":"exported more quickly than usual due to ditches or pipes within the AA (or connected to its outlet or within 10 m of the AA's edge) which drain the wetland artificially, or water is pumped out of the AA."},{"$f":"F!D124","v":0},0,{"$f":"D72*E72","v":0}]
[{"$f":"F!A129","v":"F29"},{"$f":"F!B129","v":"Internal Gradient"},{"$f":"F!C129","v":"The gradient along most of the flow path within the AA is:"},null,null,null,{"$f":"MAX(F74:F77)/MAX(E74:E77)","v":0},"Gradient3","Flatter wetlands are more likely than steep ones to slow runoff, facilitating more deposition of suspended matter and the phosphorus that is associated with it. Ground cover becomes more important to sediment stabilization in wetlands on slopes."]
[null,null,{"$f":"F!C130","v":"<2%, or, no slope is ever apparent (i.e., flat). Or, the wetland is in a depression or pond with no inlet and no outlet."},{"$f":"F!D130","v":0},4,{"$f":"D74*E74","v":0}]
[null,null,{"$f":"F!C131","v":"2-5%"},{"$f":"F!D131","v":0},3,{"$f":"D75*E75","v":0}]
[null,null,{"$f":"F!C132","v":"6-10%"},{"$f":"F!D132","v":0},2,{"$f":"D76*E76","v":0}]
[null,null,{"$f":"F!C133","v":">10%"},{"$f":"F!D133","v":0},0,{"$f":"D77*E77","v":0}]
[{"$f":"F!A194","v":"F41"},{"$f":"F!B194","v":"% Bare Ground & Thatch"},{"$f":"F!C194","v":"Consider the parts of the AA that lack surface water at the driest time of the growing season.  Viewed from directly above the ground layer, the predominant condition in those areas at that time is:"},null,null,null,{"$f":"MAX(F79:F82)/MAX(E79:E82)","v":0},"Gcover3","Dense vegetation offers frictional resistance to runoff, promoting sedimentation of suspended particles and reducing erosion. This promotes phosphorus retention because phosphorus is typically adsorbed to soil particles. "]
[null,null,{"$f":"F!C195","v":"Little or no (<5%) bare ground is visible between erect stems or under canopy anywhere in the vegetated AA. Ground is extensively blanketed by dense thatch, moss, lichens, graminoids with great stem densities, or plants with ground-hugging foliage. "},{"$f":"F!D195","v":0},3,{"$f":"D79*E79","v":0}]
[null,null,{"$f":"F!C196","v":"Slightly bare ground (5-20% bare between plants) is visible in places, but those areas comprise less than 5% of the unflooded parts of the AA."},{"$f":"F!D196","v":0},2,{"$f":"D80*E80","v":0}]
[null,null,{"$f":"F!C197","v":"Much bare ground (20-50% bare between plants) is visible in places, and those areas comprise more than 5% of the unflooded parts of the AA. "},{"$f":"F!D197","v":0},1,{"$f":"D81*E81","v":0}]
[null,null,{"$f":"F!C198","v":"Other conditions"},{"$f":"F!D198","v":0},0,{"$f":"D82*E82","v":0}]
[{"$f":"F!A200","v":"F42"},{"$f":"F!B200","v":"Ground Irregularity"},{"$f":"F!C200","v":"Consider the parts of the AA that lack surface water at some time of the year.  Excluding slash from logging, the number of small pits, raised mounds, hummocks, boulders, upturned trees, animal burrows, gullies, natural levees, wide soil cracks, and microdepressions is:"},null,null,null,{"$f":"MAX(F84:F86)/MAX(E84:E86)","v":0},"Girreg3","These features cumulatively decelerate runoff, thus allowing for more deposition of phosphorus-containing suspended sediments to occur, although usually only to a minor degree."]
[null,null,{"$f":"F!C201","v":"Few or none (minimal microtopography; <1% of that area) "},{"$f":"F!D201","v":0},0,{"$f":"D84*E84","v":0}]
[null,null,{"$f":"F!C202","v":"Intermediate"},{"$f":"F!D202","v":0},1,{"$f":"D85*E85","v":0}]
[null,null,{"$f":"F!C203","v":"Several (extensive micro-topography)"},{"$f":"F!D203","v":0},2,{"$f":"D86*E86","v":0}]
[{"$f":"F!A208","v":"F44"},{"$f":"F!B208","v":"Soil Texture"},{"$f":"F!C208","v":"In parts of the AA that lack persistent water, the texture of soil in the uppermost layer is mostly:  [To determine this, use a trowel to check in at least 3 widely spaced locations, and use the soil texture key in Appendix A of the Manual]"},null,null,null,{"$f":"MAX(F88:F91)/MAX(E88:E91)","v":0},"SoilTex3","Soil or sediment texture, and especially clay content of soil, is one of the most important predictors of phosphorus retention. Excessive organic matter buildup in soils can inhibit plant germination and growth by acidifying the soil, which restricts nutrient availability and thus plant capacity to take up and retain phosphorus (Prescott et al. 2000). However, phosphorus can also form complexes with soil organic matter and thus be retained.  "]
[null,null,{"$f":"F!C209","v":"Loamy: includes loam, sandy loam"},{"$f":"F!D209","v":0},1,{"$f":"D88*E88","v":0}]
[null,null,{"$f":"F!C210","v":"Fines: includes silt, glacial flour, clay, clay loam, silty clay, silty clay loam, sandy clay, sandy clay loam."},{"$f":"F!D210","v":0},3,{"$f":"D89*E89","v":0}]
[null,null,{"$f":"F!C211","v":"Organic"},{"$f":"F!D211","v":0},4,{"$f":"D90*E90","v":0}]
[null,null,{"$f":"F!C212","v":"Coarse: includes sand, loamy sand, gravel, cobble, stones, boulders, fluvents, fluvaquents, riverwash."},{"$f":"F!D212","v":0},0,{"$f":"D91*E91","v":0}]
[{"$f":"F!A307","v":"F65"},{"$f":"F!B307","v":"Salinity, Alkalinity, Conductance "},{"$f":"F!C307","v":"Based on measurement from a surface water area larger than .01 hectare, the AA's surface water is mostly:"},null,null,null,{"$f":"IF((D96=1),\"\",MAX(F93:F95)/MAX(E93:E95))","v":0},"Salin3","In saline wetlands, phosphorus often complexes with calcium.  It then precipitates and that facilitates retention.  Also, wetlands with moss cover and moderate to high conductivity (such as rich fens) retain phosphorus effectively (Prepas et al. 2011)."]
[null,null,{"$f":"F!C308","v":"Brackish or saline (conductance of >25 mS/cm, or >5000 ppm TDS). Or plants that indicate saline conditions comprise >20% of ground cover.  Trees and shrubs mostly absent.  Salt crust obvious around the perimeter and on flats."},{"$f":"F!D308","v":0},2,{"$f":"D93*E93","v":0}]
[null,null,{"$f":"F!C309","v":"Slightly brackish (conductance of 2.5- 25 mS/cm, or 500 - 5000 ppm TDS).  Or plants that indicate saline conditions comprise 1-20% of ground cover.  Salt crust may or may not be present along perimeter."},{"$f":"F!D309","v":0},1,{"$f":"D94*E94","v":0}]
[null,null,{"$f":"F!C310","v":"Fresh (conductance of < 2.5 mS/cm, or <500 ppm TDS). Plants that indicate saline conditions are sparse or absent. No salt crust along perimeter."},{"$f":"F!D310","v":0},0,{"$f":"D95*E95","v":0}]
[null,null,{"$f":"F!C311","v":"Unknown condition (was not measured because surface water absent or insufficient, or measurement conflicted with plant indicators). "},{"$f":"F!D311","v":0}]
[{"$f":"F!A323","v":"F68"},{"$f":"F!B323","v":"Wetland as a % of Its Contributing Area (Catchment)"},{"$f":"F!C323","v":"View the approximate boundaries of the wetland's catchment (CA) as shown in the map AESRD provides in response to your data request.  Then adjust those boundaries if necessary based on your field observations of the surrounding terrain, and/or by using procedures described in the ABWRET Manual. Relative to the extent of this catchment (but excluding the area of the AA), this AA and any bordering waters together comprise (select ONE):"},null,null,null,{"$f":"(MAX(F98:F101))/MAX(E98:E101)","v":0},"CApctB3","Sediment deposition, and thus (by correlation) phosphorus retention, can be predicted partly by the ratio of the volume of a storage basin to the volume of runoff entering the basin (Heinemann 1981). This indicator is a rough correlate of that ratio."]
[null,null,{"$f":"F!C324","v":"<1% of their catchment"},{"$f":"F!D324","v":0},0,{"$f":"D98*E98","v":0}]
[null,null,{"$f":"F!C325","v":"1 to 10% of their catchment"},{"$f":"F!D325","v":0},1,{"$f":"D99*E99","v":0}]
[null,null,{"$f":"F!C326","v":"10 to 100%  of their catchment"},{"$f":"F!D326","v":0},2,{"$f":"D100*E100","v":0}]
[null,null,{"$f":"F!C327","v":"Larger than the area of their catchment (wetland has essentially no catchment, e.g., isolated by dikes with no input channels, or is a raised bog). "},{"$f":"F!D327","v":0},3,{"$f":"D101*E101","v":0}]
[{"$f":"S!A64","v":"S9"},{"$f":"S!B64","v":"Soil or Sediment Alteration Within the Assessment Area"},null,{"$f":"S!F81","v":0},null,null,{"$f":"1-D102","v":1},"SoilAlt3","Phosphorus is often adsorbed to soils, so if soils within a wetland are being disturbed or eroded, it is less likely the wetland will retain phosphorust on a net annual basis."]
[]
[null,null,"Adsorption [ADSORB]"]
[null,"Wetlands <10 hectares:","[ AVERAGE(SoilTex3, SoilOrgPct, Salin3) + AVERAGE(WatProb, SatPct3, Algae3, Fluctu3, DomDepth3) ] / 2",null,null,null,{"$f":"IF((GT10HA=1),G106, (AVERAGE(SoilTex3, SoilOrgPct, Salin3) + AVERAGE(WatProb, SatPct3, Algae3, Fluctu3, DomDepth3)) / 2)","v":0}]
[null,"Wetlands >10 hectares:","Substituted SoilTex",null,null,null,{"$f":"(AVERAGE(SoilTex_PR, SoilOrgPct, Salin3) + AVERAGE(WatProb, SatPct3, Algae3, Fluctu3, DomDepth3)) / 2","v":0}]
[]
[null,null,"Sedimentation [SEDTRAP]"]
[null,"Wetlands <10 hectares:","[ AVERAGE(OpenWpct3, Interspers3, WetVegArea) + AVERAGE(1-Sub0Days, CApctB3, Persis3, Lake3, VegWabs3, ThruFlo3, Constric3, Gradient3, Gcover3, Girreg3, SoilAlt3) ] / 2",null,null,null,{"$f":"IF((GT10HA=1),G110,(AVERAGE(OpenWpct3, Interspers3, WetVegArea) + AVERAGE(1-Sub0Days, CApctB3, Persis3, Lake3, VegWabs3, ThruFlo3, Constric3, Gradient3, Gcover3, Girreg3, SoilAlt3)) / 2)","v":0.1111111111111111}]
[null,"Wetlands >10 hectares:","Substituted 1-OWpct, MixWaterVeg",null,null,null,{"$f":"(AVERAGE(1-OWpct, MixWaterVeg, WetVegArea) + AVERAGE(1-Sub0Days, CApctB3, Persis3, Lake3, VegWabs3, ThruFlo3, Constric3, Gradient3, Gcover3, Girreg3, SoilAlt3)) / 2","v":0.61111111111111116}]
[]
[null,null,"Export [OUT]"]
[null,null,"OutDura3",null,null,null,{"$f":"OutDura3","v":0}]
[]
[null,null,"ABWRET-A FUNCTION MODEL"]
[null,null,"Phosphorus Retention"]
[null,null,"IF((OutNone + OutNone1>0),10, ELSE: AVERAGE(ADSORB, SEDTRAP, OUT)",null,null,null,{"$f":"IF((OutNone + OutNone1>0),10, 10*AVERAGE(ADSORB1A, SEDTRAP1A, OutDura3))","v":0.37037037037037035}]
[null,null,null,null,null,null,null,null,"Literature Cited"]
[null,null,"ABWRET-E model:",null,null,null,null,null,"Alberti, M., D. Booth, K. Hill, B. Coburn, C. Avolio, S. Coe, and D. Spirandelli. 2007. The impact of urban patterns on aquatic ecosystems: An empirical analysis in Puget Lowland sub-basins. Landscape and Urban Planning 80:345-361."]
[null,1,"IF(ChannConn + RipFloodPl = 0), then =10",{"$f":"IF((ChannConn+RipFloodpl=0), 10, \"\")","v":10}," ",null,null,null,"Aldous, A., P. McCormick, C. Ferguson, S. Graham, and C. Craft. 2005. Hydrologic regime controls soil phosphorus fluxes in restoration and undisturbed wetlands. Restoration Ecology 13:341-347."]
[null,2,"ELSE calculate these averages:",null,null,null,null,null,"Aldous, A. R., C. B. Craft, C. J. Stevens, M. J. Barry, and L. B. Bach. 2007. Soil phosphorus release from a restoration wetland, Upper Klamath Lake, Oregon. Wetlands 27:1025-1035."]
[null,"a.","AVERAGE(1-OWpct, MixWaterVeg, WetVegArea)",{"$f":"IFERROR(AVERAGE(1-OWpct, MixWaterVeg, WetVegArea),\"\")","v":1},null,null,null,null,"Amatya, D. M., R. W. Skaggs, J. W. Gilliam, and J. H. Hughes. 2003. Effects of orifice-weir outlet on hydrology and water quality of a drained forested watershed. Southern Journal of Applied Forestry 27:130-142."]
[null,"b.","AVERAGE(SoilTex, SoilOrgPct)",{"$f":"IFERROR(AVERAGE(SoilTex_PR, SoilOrgPct),\"\")","v":""},null,null,null,null,"Burley, K. L., E. E. Prepas, and P. A. Chambers. 2001. Phosphorus release from sediments in hardwater eutrophic lakes: the effects of redox-sensitive and -insensitive chemical treatments. Freshwater Biology 46:1061-1074."]
[null,3,"10*AVERAGE(WatProb, Sub0Days, a, b) ",{"$f":"IF((D120=10),10, 10*AVERAGE(WatProb,Sub0Days,D122,D123))","v":10},null,null,null,null,"Cooke, S. E. and E. E. Prepas. 1998. Stream phosphorus and nitrogen export from agricultural and forested watersheds on the Boreal Plain. Canadian Journal of Fisheries and Aquatic Sciences 55:2292-2299."]
[null,null,null,null,null,null,null,null,"Diebel, M. W., J. T. Maxted, D. M. Robertson, S. Han, Z. Vander, and M. Jake. 2009. Landscape planning for agricultural nonpoint source pollution reduction III: assessing phosphorus and sediment reduction potential. Environmental Management 43:69-83."]
[null,null,"ABWRET-E with substitutions:",null,null,null,null,null,"Feller, M. 2005. Forest harvesting and streamwater inorganic chemistry in western North America: a review. Journal of the American Water Resources Association 41:785-811."]
[null,1,"IF(OutNone+OutNone1>0), then =10",{"$f":"IF((OutNone+OutNone1>0), 10, \"\")","v":""},null,null,null,null,"Heinemann, H. G. 1981. A new sediment trap efficency curve for small reservoirs. Water Resources Bulletin 17:825-830."]
[null,2,"ELSE calculate these averages:",null,null,null,null,null,"Hoffmann, C. C., C. Kjaergaard, J. Uusi-Kamppa, H. C. B. Hansen, and B. Kronvang. 2009. Phosphorus retention in riparian buffers: Review of their efficiency. Journal of Environmental Quality 38:1942-1955."]
[null,"a.","AVERAGE(OpenWpct3, Interspers3, WetVegArea)",{"$f":"IFERROR(AVERAGE(OpenWpct3, Interspers3, WetVegArea),\"\")","v":0},null,null,null,null,"Houlahan, J. E. and C. S. Findlay. 2004. Estimating the ‘critical’ distance at which adjacent land-use degrades wetland water and sediment quality. Landscape Ecology 19:677-690."]
[null,"b.","AVERAGE(SoilTex3, SoilOrgPct)",{"$f":"IFERROR(AVERAGE(SoilTex3, SoilOrgPct),\"\")","v":0},null,null,null,null,"Jones, K. B., A. C. Neale, M. S. Nash, R. D. Van Remortel, J. D. Wickham, K. H. Riitters, and R. V. O'Neill. 2001. Predicting nutrient and sediment loadings to streams from landscape metrics: a multiple watershed study from the United States Mid-Atlantic Region. Landscape Ecology 16:301-312."]
[null,3,"10*AVERAGE(WatProb, 1-Sub0Days, a, b) ",{"$f":"IF((D127=10),10, 10*AVERAGE(WatProb, (1-Sub0Days),D129,D130))","v":3.333333333333333},null,null,null,null,"Knox, A. K., R. A. Dahgren, K. W. Tate, and E. R. Atwill. 2008. Efficacy of natural wetlands to retain nutrient, sediment and microbial pollutants. Journal of Environmental Quality 37:1837-1846."]
[null,null,null,null,null,null,null,null,"McBride, M. and D. B. Booth. 2005. Urban impacts on physical stream condition: Effects of spatial scale, connectivity, and longitudinal trends. Journal of the American Water Resources Association 41:565-580."]
[null,null,null,null,null,null,null,null,"Morris, A. W., A. J. Bale, and R. J. M. Howland. 1981. Nutrient distributions in an estuary - evidence of chemical precipitation of dissolved silicate and phosphate. Estuarine Coastal and Shelf Science 12:205-216."]
[null,null,null,null,null,null,null,null,"Prepas, E. E., B. Pinel-Alloul, D. Planas, G. Méthot, S. Paquet, and S. Reedyk. 2001. Forest harvest impacts on water quality and aquatic biota on the Boreal Plain: Introduction to the TROLS lake program. Canadian Journal of Fisheries and Aquatic Sciences 58:421-436."]
[null,null,null,null,null,null,null,null,"Prescott, C. E., L. Vesterdal, J. Pratt, K. H. Venner, L. M. de Montigny, and J. A. Trofymow. 2000. Nutrient concentrations and nitrogen mineralization in forest floors of single species conifer plantations in coastal British Columbia. Canadian Journal of Forest Research 30:1341-1352."]
[null,null,null,null,null,null,null,null,"Roberts, M. L. and R. E. Bilby. 2009. Urbanization alters litterfall rates and nutrient inputs to small Puget lowland streams. Journal of the North American Benthological Society 28:941-954."]
[null,null,null,null,null,null,null,null,"Roberts, A. and S. Prince. 2010. Effects of urban and non-urban land cover on nitrogen and phosphorus runoff to Chesapeake Bay. Ecological Indicators 10:459-474."]
[null,null,null,null,null,null,null,null,"Snyder, D. T. and J. L. Morace. 1997. Nitrogen and Phosphorus Loading from Drained Wetlands Adjacent to Upper Klamath and Agency Lakes, Oregon. US Geological Survey Water Resources Investigations Report 97-4059. US Geological Survey, Fort Collins, CO."]
[null,null,null,null,null,null,null,null,"Walbridge, M. R. and J. A. Navaratnam. 2006. Phosphorous in boreal peatlands. Pages 231-258 in R. K. Wieder and D. H. Vitt, editors. Boreal Peatland Ecosystems, Ecological Studies, Volume 188. Springer, Berlin Heidelberg, Germany."]
[null,null,null,null,null,null,null,null,"White, W. J., L. A. Morris, D. B. Warnell, A. P. Pinho, C. R. Jackson, and L. T. West. 2007. Sediment retention by forested filter strips in the Piedmont of Georgia. Journal of Soil and Water Conservation 62:453-463."]

{"sheet":"NR","index":14,"n_rows":209,"n_cols":9,"rows_kept":209,"cut":false,"hidden":false,"merged":[[120,0,126,0],[120,8,126,8],[127,7,131,7],[0,0,0,1],[46,0,53,0],[61,0,66,0],[35,1,40,1],[0,4,0,7],[28,7,34,7],[35,7,40,7],[41,7,45,7],[71,0,76,0],[54,0,60,0],[67,0,70,0],[91,0,95,0],[102,0,106,0],[77,8,82,8],[46,8,53,8],[77,1,82,1],[83,1,86,1],[54,1,60,1],[71,1,76,1],[54,8,60,8],[46,1,53,1],[46,7,53,7],[54,7,60,7],[107,7,110,7],[111,7,114,7],[115,0,119,0],[91,1,95,1],[61,8,66,8],[96,8,101,8],[67,8,70,8],[115,1,119,1],[102,8,106,8],[107,8,110,8],[111,1,114,1],[107,1,110,1],[96,0,101,0],[107,0,110,0],[96,1,101,1],[83,8,86,8],[111,0,114,0],[61,1,66,1],[87,1,90,1],[87,0,90,0],[77,0,82,0],[67,1,70,1],[91,7,95,7],[102,7,106,7],[91,8,95,8],[102,1,106,1],[83,0,86,0],[96,7,101,7],[87,8,90,8],[28,0,34,0],[28,8,34,8],[16,7,20,7],[21,7,27,7],[127,8,131,8],[127,1,131,1],[115,8,119,8],[120,1,126,1],[71,8,76,8],[111,8,114,8],[61,7,66,7],[67,7,70,7],[71,7,76,7],[77,7,82,7],[83,7,86,7],[87,7,90,7],[115,7,119,7],[120,7,126,7],[166,1,167,1],[127,0,131,0],[16,8,20,8],[35,8,40,8],[41,0,45,0],[21,1,27,1],[16,1,20,1],[16,0,20,0],[41,8,45,8],[21,8,27,8],[41,1,45,1],[35,0,40,0],[21,0,27,0],[28,1,34,1]]}
["Nitrate Removal                                &                                       Retention ",null,"The effectiveness for retaining particulate nitrate and converting soluble nitrate and ammonium to nitrogen gas, primarily through the microbial process of denitrification, while generating little or no nitrous oxide (a potent greenhouse gas).  ","NR",null,null,null,null,"The model does not address the ecological need for keeping nitrate out of the surface or ground water at a particular location, as would be implied partly by the presence of domestic wells, nuisance blooms of algae, or plants that are sensitive to nitrate overenrichment.  "]
["#","Function Indicators from Estimator","Scoring Notes",null,null,null,"Normalised Score","Indicator Abbreviation or Formula","Rationale"]
[{"$f":"OF!A3","v":"OF2"},{"$f":"OF!C3","v":"Aspect of the AA's 100m Upslope Buffer"},"Inverse",null,null,null,{"$f":"IF((Aspect=\"\"),\"\",1-Aspect)","v":""},"Aspect","Soil temperatures are warmer for longer on south-facing slopes, and this is essential for denitrification which removes soluble N (Kim et al. 2007). However, those soils should not be dried out to less than 70% saturation by those warmer conditions (Hefting et al. 2006)."]
[{"$f":"OF!A5","v":"OF4"},{"$f":"OF!C5","v":"Channel Connection"},null,null,null,null,{"$f":"IF((ChannConn=\"\"),\"\",ChannConn)","v":""},"ChannConn","Wetlands that lack an outlet (never have any outflow) retain or remove via denitrification all N that enters them."]
[{"$f":"OF!A18","v":"OF17"},{"$f":"OF!C18","v":"Growing Degree Days"},null,null,null,null,{"$f":"IF((GrowDD=\"\"),\"\",GrowDD)","v":""},"GrowDD","Microbes responsible for most of the nitrate removal in wetlands thrive best at warmer soil or sediment temperatures. "]
[{"$f":"OF!A23","v":"OF22"},{"$f":"OF!C23","v":"L/G Index (Residence Time)"},null,null,null,null,{"$f":"IF((LGIndex=\"\"),\"\",LGIndex)","v":""},"LGindex","N removal often correlates with detention time, which in turn correlates with flow path length within a wetland."]
[{"$f":"OF!A28","v":"OF27"},{"$f":"OF!C28","v":"Interspersion Index for Internal Water & Vegetation (macroscale)"},null,null,null,null,{"$f":"IF((MixWaterVeg=\"\"),\"\",MixWaterVeg)","v":""},"MixWaterVeg","Greater interspersion of open water and vegetation is hypothesized to support greater nitrate removal. That is because open water areas tend to be more aerobic, whereas densely vegetated areas often are anaerobic, except where plant roots oxidize a small part of the sediment. The combination of anaerobic and aerobic areas in close proximity facilitates nitrate loss through denitrification."]
[{"$f":"OF!A31","v":"OF30"},{"$f":"OF!C31","v":"% of AA that is Open Water (macro scale)"},"Inverse",null,null,null,{"$f":"IF((OWpct=\"\"),\"\",1-OWpct)","v":""},"OWpct","Plants take up nitrate from sediments and can facilitate retention if N is transferred to roots that are not as subject to erosion as foliage. Plants also facilitate sediment deposition by slowing the water, and some nitrate is associated with that sediment so is also deposited and potentially retained. Perhaps most importantly, roots of some plants oxidize the anoxic sediments that surround them and this facilitates denitrification, the major process for removing soluble nitrate from water."]
[{"$f":"OF!A47","v":"OF46"},{"$f":"OF!C47","v":"Organic Soil Content (macroscale)"},null,null,null,null,{"$f":"IF((SoilOrgPct=\"\"),\"\",SoilOrgPct)","v":""},"SoilOrgPct","Denitrification rates can be limited by the amount of available carbon. Denitrification enzyme activity, on a per gram basis, is typically greater in organic soils than mineral soils (Van Hoewyk et al. 2000).  If the organic matter (carbon) is labile, i.e., readily assimilated by certain microbes, more nitrate will be removed from the water."]
[{"$f":"OF!A50","v":"OF49"},{"$f":"OF!C50","v":"Soil Texture (macroscale)"},"See Table 3 worksheet.",null,null,null,{"$f":"IF((SoilTex_NROE=\"\"),\"\",SoilTex_NROE)","v":""},"SoilTex_NROE","See above."]
[{"$f":"OF!A52","v":"OF51"},{"$f":"OF!C52","v":"Subzero Days"},"Inverse",null,null,null,{"$f":"IF((Sub0Days=\"\"),\"\",1-Sub0Days)","v":""},"Sub0Days","Microbes responsible for most of the nitrate removal in wetlands thrive best at warmer soil or sediment temperatures (e.g., Beutel et al. 2009)."]
[{"$f":"OF!A53","v":"OF52"},{"$f":"OF!C53","v":"Swamp + Marsh as % of the Wetland"},null,null,null,null,{"$f":"IF((SwampMarshPct=\"\"),\"\",SwampMarshPct)","v":""},"SwampMarshPct","Water table levels tend to be more dynamic in marsh and swamp classes than in bog or fen wetland classes.  Dynamic water levels tend to result in greater denitrification rates."]
[{"$f":"OF!A61","v":"OF60"},{"$f":"OF!C61","v":"Water Permanence Probability"},null,null,null,null,{"$f":"IF((WatProb=\"\"),\"\",1-WatProb)","v":""},"WatProb","Water table depth and duration of saturation affect sediment oxygen (redox) and thus N cycling (D’Amore et al. 2009).  Denitrification rates are highest at the interface between aerobic and anaerobic conditions. Such conditions often develop where much of a wetland is inundated only seasonally, e.g., water area expands into vegetated areas only seasonally. In addition, levels of soil organic matter are often higher in seasonal wetlands than in permanently inundated ones (Shaffer & Ernst 1999), and organic matter is key to supporting denitrification."]
[{"$f":"OF!A70","v":"OF69"},{"$f":"OF!C70","v":"% of Wetland Classified as Swamp or Forested (macro scale)"},null,null,null,null,{"$f":"IF((WetWooded=\"\"),\"\",WetWooded)","v":""},"WetWooded","Tree roots can extend the subsurface zone of denitrification by oxidizing deeper subsurface areas, as well as retaining drifting snow which helps sustain soil moisture necessary for denitrification. Trees also take up and temporarily retain nitrate, as well as adding carbon to the soil, which promotes denitrification.  However, dense canopy cover reduces soil warming in spring (Hennon et al. 2010) which otherwise could accelerate denitrification."]
[{"$f":"OF!A68","v":"OF67"},{"$f":"OF!C68","v":"Perimeter-Area Ratio"},null,null,null,null,{"$f":"IF((WetPerim2Area=\"\"),\"\",WetPerim2Area)","v":""},"WetPerim2Area","Upland soils are normally aerobic, whereas wetland soils are often anaerobic. Maximum denitrification occurs at the interface of aerobic and anaerobic conditions. Thus, proportionally longer (i.e., convoluted) edges should provide the most opportunity for removal of nitrate via denitrification."]
["#","Function Indicators from Onsite Visit","Categorical Choices","Data","Weight","Data  x  Weight","Normalised Score","Indicator Abbreviation or Formula","Rationale & Scoring Notes"]
[{"$f":"F!A6","v":"F1"},{"$f":"F!B6","v":"Wetland Type - Predominant"},{"$f":"F!C6","v":"Most of the vegetated part of the AA (wetland Assessment Area) is a (select ONE):"},null,null,null,{"$f":"MAX(F18:F21)/MAX(E18:E21)","v":0},"Wettype4","Floodplain wetlands are notably effective for removing N via denitrification (Clilverd et al. 2008) and that process is limited by available carbon more than it is in bogs (Pinay et al. 2003). Bogs are typically nitrogen-poor (Heilman 1966) and thus are able to rapidly take up much of the nitrate that reaches them (D’Amore et al. 2010). Their acidic conditions inhibit generation of nitrous oxide, but also may inhibit nitrification and the removal of nitrate via denitrification (Pinay et al. 2003). Denitrification is more prominent in fens and marshes than in acidic bogs. Bogs tend to cycle nitrogen internally and remove added N (Li & Vitt 1997, Bayley & Mewhort 2004), although due to acidic conditions and other factors, mosses in some wetlands have less capacity to take up apparently available N than do vascular plants (Heijmans et al. 2002, Berendse et al. 2001). Forested wetlands, especially those with an alder component or on slopes, may have less capacity to remove N via denitrification and may actually add nitrate via N fixation (Fellman & D’Amore 2007). However, in forested wetlands in BC, the volume of hemlocks increased tenfold 10 years after fertilization with N, especially when combined with addition of P. And western red cedar stand volume more than doubled 15 years after N fertilization, although there was no additional effect of P fertilization (Blevins et al. 2006). Hemlock and cedar stands were similarly found to be N-limited by McDonald et al. (1994) and Lertzmann et al. (1996). Marshes tend to retain or remove nitrogen (Bedford et al. 1999). "]
[null,null,{"$f":"F!C7","v":"Wooded Swamp"},{"$f":"F!D7","v":0},3,{"$f":"D18*E18","v":0}]
[null,null,{"$f":"F!C8","v":"Bog"},{"$f":"F!D8","v":0},4,{"$f":"D19*E19","v":0}]
[null,null,{"$f":"F!C9","v":"Fen"},{"$f":"F!D9","v":0},2,{"$f":"D20*E20","v":0}]
[null,null,{"$f":"F!C10","v":"Marsh or Shallow Open Water"},{"$f":"F!D10","v":0},1,{"$f":"D21*E21","v":0}]
[{"$f":"F!A17","v":"F3"},{"$f":"F!B17","v":"% Saturated Only"},{"$f":"F!C17","v":"The percentage of the AA that never contains surface water during an average year (that is, except perhaps for a few hours after snowmelt or rainstorms), but which is still a wetland, is:"},null,null,null,{"$f":"MAX(F23:F28)/MAX(E23:E28)","v":0},"SatPct4","Denitrification processes occur when anaerobic conditions occur, which are more likely when surface water is present and blocks gas exchange. Shallow inundation tends to decrease emissions of nitrous oxide (Zaman et al. 2007, Song et al. 2008) ."]
[null,null,{"$f":"F!C18","v":"less than 1%, or <0.01 hectare (about 10 m on a side) never has surface water.  In other words, all or nearly all of the AA is inundated permanently or at least seasonally."},{"$f":"F!D18","v":0},4,{"$f":"D23*E23","v":0}]
[null,null,{"$f":"F!C19","v":"1-25% of the AA never contains surface water."},{"$f":"F!D19","v":0},5,0]
[null,null,{"$f":"F!C20","v":"25-50% of the AA never contains surface water."},{"$f":"F!D20","v":0},3,0]
[null,null,{"$f":"F!C21","v":"50-99% of the AA never contains surface water."},{"$f":"F!D21","v":0},2,0]
[null,null,{"$f":"F!C22","v":">99% of the AA never contains surface water, except for water flowing in channels and/or in pools that occupy <1% of the AA. SKIP to F26 (Channel Connection & Outflow Duration)"},{"$f":"F!D22","v":0},1,0]
[null,null,{"$f":"F!C23","v":">99% of the AA never contains surface water, and AA is not intersected by channels that have flow, not even for a few days per year. SKIP to F26."},{"$f":"F!D23","v":0},0,0]
[{"$f":"F!A24","v":"F4"},{"$f":"F!B24","v":"% with Persistent Surface Water"},{"$f":"F!C24","v":"The percentage of the AA that has surface water (either ponded or flowing, either open or obscured by vegetation) during all of the growing season during most years is:"},null,null,null,{"$f":"IF((AllSat+AllSat1>0),\"\", MAX(F30:F35)/MAX(E30:E35))","v":0},"PermWpct4","Exposing sediments to the air can cause them to release accumulated nitrate, potentially resulting in less removal. In contrast, long-duration flooding usually makes sediments anaerobic, which is necessary for the denitrification process.  Denitrification processes occur when anaerobic conditions occur, which are more likely when surface water is present and blocks gas exchange. Shallow inundation tends to decrease emissions of nitrous oxide (Zaman et al. 2007, Song et al. 2008). In calculations, is excluded automatically (cell goes blank) if wetland never has surface water during an average year. "]
[null,null,{"$f":"F!C25","v":"less than 1%, or <0.01 hectare (whichever is less).  SKIP to F8 (% Flooded Only Seasonally)."},{"$f":"F!D25","v":0},0,{"$f":"D30*E30","v":0}]
[null,null,{"$f":"F!C26","v":"1-25% of the AA, and mostly in narrow channels and/or small scattered pools."},{"$f":"F!D26","v":0},1,0]
[null,null,{"$f":"F!C27","v":"1-25% of the AA, and mostly in a single large pool, pond, and/or channel."},{"$f":"F!D27","v":0},1,0]
[null,null,{"$f":"F!C28","v":"25-50% of the AA"},{"$f":"F!D28","v":0},3,0]
[null,null,{"$f":"F!C29","v":"50-95% of the AA"},{"$f":"F!D29","v":0},2,0]
[null,null,{"$f":"F!C30","v":">95% of the AA"},{"$f":"F!D30","v":0},2,0]
[{"$f":"F!A39","v":"F8"},{"$f":"F!B39","v":"% Flooded Only Seasonally"},{"$f":"F!C39","v":"The percentage of the AA that is covered by surface water only during the wettest time of year (and for >2 consecutive days during that time) is:"},null,null,null,{"$f":"IF((AllSat+AllSat1>0),\"\",MAX(F37:F41)/MAX(E37:E41))","v":0},"SeasWpct4","Water table depth and duration of saturation affect redox and thus N cycling (D’Amore et al. 2009). Denitrification rates are highest at the interface between aerobic and anaerobic conditions. Such conditions often develop where a ponded area expands seasonally into vegetated areas. In addition, levels of soil organic matter are often higher in seasonal wetlands than in permanently inundated ones (Shaffer & Ernst 1999), and organic matter is key to supporting denitrification. In calculations, is excluded automatically (cell goes blank) if wetland never has surface water during an average year."]
[null,null,{"$f":"F!C40","v":"<1%. "},{"$f":"F!D40","v":0},0,{"$f":"D37*E37","v":0}]
[null,null,{"$f":"F!C41","v":"1-25% "},{"$f":"F!D41","v":0},1,{"$f":"D38*E38","v":0}]
[null,null,{"$f":"F!C42","v":"25-50% "},{"$f":"F!D42","v":0},2,{"$f":"D39*E39","v":0}]
[null,null,{"$f":"F!C43","v":"50-95% "},{"$f":"F!D43","v":0},3,{"$f":"D40*E40","v":0}]
[null,null,{"$f":"F!C44","v":">95% "},{"$f":"F!D44","v":0},4,{"$f":"D41*E41","v":0}]
[{"$f":"F!A45","v":"F9"},{"$f":"F!B45","v":"Annual Water Fluctuation Range"},{"$f":"F!C45","v":"The annual fluctuation in surface water level within most of the parts of the AA that contain surface water is:"},null,null,null,{"$f":"IF((AllSat+AllSat1>0),\"\", IF((NoSeasonal=1),\"\",MAX(F43:F46)/MAX(E43:E46)))","v":0},"Fluctu4","Wetting and drying of sediments, as happens especially in wetlands with large and frequent water level fluctuations (because a wider area is subject to wetting-drying and associated aerobic-anaerobic shift), increases the loss of nitrate via denitrification. In Oregon, decreased total nitrogen in streams was associated with increased stream flashiness that had resulted from urbanization (Waite et al. 2006).  In calculations, is excluded automatically (cell goes blank) if wetland never has surface water during an average year, or if none of it floods only seasonally."]
[null,null,{"$f":"F!C46","v":"<10 cm change (stable) "},{"$f":"F!D46","v":0},0,{"$f":"D43*E43","v":0}]
[null,null,{"$f":"F!C47","v":"10 cm - 50 cm change"},{"$f":"F!D47","v":0},2,{"$f":"D44*E44","v":0}]
[null,null,{"$f":"F!C49","v":"1-2 m change"},{"$f":"F!D49","v":0},3,{"$f":"D45*E45","v":0}]
[null,null,{"$f":"F!C50","v":">2 m change"},{"$f":"F!D50","v":0},4,{"$f":"D46*E46","v":0}]
[{"$f":"F!A62","v":"F12"},{"$f":"F!B62","v":"% of Water Ponded vs. Flowing "},{"$f":"F!C62","v":"The percentage of the AA's surface water that is ponded (stagnant, or flows so slowly that fine sediment is not held in suspension) during most of the time it is present, and which is either open or shaded by emergent vegetation is:"},null,null,null,{"$f":"IF((AllSat+AllSat1>0),\"\", IF((SmallAA=1),\"\", MAX(F48:F54)/MAX(E48:E54)))","v":0},"PondPct4","Ponded conditions provide longer time for nitrate processing, as well as causing sediments to lose oxygen, thus creating a microclimate favorable for denitrification. In calculations, is excluded automatically (cell goes blank) if wetland never has surface water during an average year. Also is excluded automatically if wetland is <0.01 ha."]
[null,null,{"$f":"F!C63","v":"<1% or none, or occupies <0.01 hectare cumulatively.  Nearly all water is flowing.  Enter \"1\" and SKIP to F21 (Stained Surface Water)."},{"$f":"F!D63","v":0},0,{"$f":"D48*E48","v":0}]
[null,null,{"$f":"F!C64","v":"1-5% of the water, and mainly in small pools.  The rest is flowing."},{"$f":"F!D64","v":0},1,0]
[null,null,{"$f":"F!C65","v":"1-5% of the water, and mainly in a single large pool or pond.  The rest is flowing."},{"$f":"F!D65","v":0},1,0]
[null,null,{"$f":"F!C66","v":"5-30% of the water"},{"$f":"F!D66","v":0},2,0]
[null,null,{"$f":"F!C67","v":"30-70% of the water"},{"$f":"F!D67","v":0},3,0]
[null,null,{"$f":"F!C68","v":"70-95% of the water"},{"$f":"F!D68","v":0},4,0]
[null,null,{"$f":"F!C69","v":">95% of the water.  Little or no visibly flowing water within the AA."},{"$f":"F!D69","v":0},5,0]
[{"$f":"F!A71","v":"F14"},{"$f":"F!B71","v":"% of Ponded Water That Is Open "},{"$f":"F!C71","v":"In ducks-eye aerial view, the percentage of the ponded water that is open (lacking emergent vegetation during most of the growing season, and unhidden by a forest or shrub canopy) is:"},null,null,null,{"$f":"IF((AllSat+AllSat1>0),\"\", IF((NoPonded=1),\"\", IF((SmallAA=1),\"\", MAX(F56:F61)/MAX(E56:E61))))","v":0},"OWpct4","Plants take up nitrate from sediments and can facilitate retention if N is transferred to roots that are not as subject to erosion as foliage. Plants also facilitate sediment deposition by slowing the water, and some nitrate is associated with that sediment so is also deposited and potentially retained. Perhaps most importantly, roots of some plants oxidize the anoxic sediments that surround them and this facilitates denitrification, the major process for removing soluble nitrate from water.  In calculations, is excluded automatically (cell goes blank) if wetland never has surface water during an average year. Also is excluded automatically if wetland has no ponded water or is <0.01 ha."]
[null,null,{"$f":"F!C72","v":"<1% or none, or largest pool occupies <0.01 hectares.  Enter \"1\" and SKIP to F20 (Floating Algae & Duckweed)."},{"$f":"F!D72","v":0},5,{"$f":"D56*E56","v":0}]
[null,null,{"$f":"F!C73","v":"1-5% of the ponded water.  Enter \"1\" and SKIP to F20."},{"$f":"F!D73","v":0},4,0]
[null,null,{"$f":"F!C74","v":"5-30% of the ponded water."},{"$f":"F!D74","v":0},3,0]
[null,null,{"$f":"F!C75","v":"30-70% of the ponded water."},{"$f":"F!D75","v":0},2,0]
[null,null,{"$f":"F!C76","v":"70-99% of the ponded water."},{"$f":"F!D76","v":0},1,0]
[null,null,{"$f":"F!C77","v":"100% of the ponded water. "},{"$f":"F!D77","v":0},0,0]
[{"$f":"F!A84","v":"F16"},{"$f":"F!B84","v":"Predominant Width of Vegetated Zone within Wetland"},{"$f":"F!C84","v":"At the driest time of year (or lowest water level), the average width of vegetated area in the AA that separates adjoining uplands from open water within the AA is:"},null,null,null,{"$f":"IF((AllSat+AllSat1>0),\"\", IF((OpenW=0),\"\", IF((SmallAA=1),\"\", MAX(F63:F67)/MAX(E63:E67))))","v":""},"VwidthAbs4","Wider vegetated areas provide more area for biological processing of nitrate, and for nitrate adsorbed to sediment particles in runoff to be filtered and deposited. The most comprehensive and sophisticated analysis that used statistical procedures (meta-analysis) to synthesize results from over 60 peer-reviewed studies of nitrate removal by buffers in temperate climates found that widths of approximately 10 ft, 92 ft, and 367 ft are needed to achieve 50%, 75%, and 90% removal efficiencies for nitrate (Mayer et al. 2005, Mayer et al. 2007). This assumed that most inputs are through subsurface flow. When surface flow dominates (as often occurs during storms, and where subsurface storm drains have been installed around homes), buffers of 109 ft, 387 ft, and 810 ft are needed to achieve the same removal efficiencies (Mayer et al. 2005).  In calculations, is excluded automatically (cell goes blank) if wetland never has surface water during an average year. Also is excluded automatically if wetland lacks open water or is <0.01 ha."]
[null,null,{"$f":"F!C85","v":"<1 m"},{"$f":"F!D85","v":0},0,{"$f":"D63*E63","v":0}]
[null,null,{"$f":"F!C86","v":"1 - 9 m"},{"$f":"F!D86","v":0},1,{"$f":"D64*E64","v":0}]
[null,null,{"$f":"F!C87","v":"10 - 29 m"},{"$f":"F!D87","v":0},2,{"$f":"D65*E65","v":0}]
[null,null,{"$f":"F!C88","v":"30 - 49 m"},{"$f":"F!D88","v":0},3,{"$f":"D66*E66","v":0}]
[null,null,{"$f":"F!C90","v":"> 100 m"},{"$f":"F!D90","v":0},4,{"$f":"D67*E67","v":0}]
[{"$f":"F!A95","v":"F18"},{"$f":"F!B95","v":"Interspersion of Robust Emergents & Open Water"},{"$f":"F!C95","v":"During most of the growing season, the spatial pattern of tall robust herbaceous vegetation (e.g., cattail, bulrush) that has surface water beneath it is mostly:"},null,null,null,{"$f":"IF((AllSat+AllSat1>0),\"\", IF((NoPonded=1),\"\", IF((NoOpenPonded+ NoOpenPonded1>0),\"\", IF((AllOpenPond=1),\"\", IF((SmallAA=1),\"\", MAX(F69:F71)/MAX(E69:E71))))))","v":0},"Interspers4","Greater interspersion of open water and vegetation is hypothesized to support greater nitrate removal. That is because open water areas tend to be more aerobic, whereas densely vegetated areas often are anaerobic, except where plant roots oxidize a small part of the sediment. The combination of anaerobic and aerobic areas in close proximity facilitates nitrate loss through denitrification. In calculations, is excluded automatically (cell goes blank) if wetland never has surface water during an average year, if no ponded water, if ponded water but no vegetation, if ponded but no open water, or if <0.01 ha."]
[null,null,{"$f":"F!C96","v":"Scattered in small clumps, islands, or patches throughout the surface water area."},{"$f":"F!D96","v":0},3,{"$f":"D69*E69","v":0}]
[null,null,{"$f":"F!C97","v":"Intermediate"},{"$f":"F!D97","v":0},2,{"$f":"D70*E70","v":0}]
[null,null,{"$f":"F!C98","v":"Clumped at one or a few sides of the surface water area, or mostly surrounds a central area of open water.  Or such vegetation is absent or covers <9 sq m and <1% of the AA."},{"$f":"F!D98","v":0},1,{"$f":"D71*E71","v":0}]
[{"$f":"F!A109","v":"F25"},{"$f":"F!B109","v":"Through Flow Pattern"},{"$f":"F!C109","v":"During its travel through the AA at the time of peak annual flow, most of the water arriving in channels [select only the ONE encountered by most of the incoming water]:"},null,null,null,{"$f":"IF((AllSat=1),\"\", IF((Inflows=0),\"\",MAX(F73:F77)/MAX(E73:E77)))","v":""},"ThruFlo4","Like a constricted outlet, vegetation and other obstacles create a \"roughness\" within a wetland that can slow the water and allow more time for biological processing of nitrate. This is much truer if the vegetation intercepts a large proportion of the flow during high-flow periods (i.e., is not merely along an upland edge that never floods). Water takes longer to move through complex channel networks (e.g., braided or sinuous) which themselves provide additional friction, thus allowing more suspended sediment and the nitrate associated with it to be deposited. Increased channel complexity also implies greater interspersion of open water and vegetation (see above) and in some cases, more hyporheic flow -- both of which favor nitrate removal. Wetlands with a sheet flow pattern often retain more nitrate than channelized systems (Morris et al. 1981, Knox et al. 2008). In calculations, is excluded automatically (cell goes blank) if wetland never has surface water during an average year or if no surface inflows."]
[null,null,{"$f":"F!C110","v":"Does not bump into plant stems as it travels through the AA.  Nearly all the water continues to travel in unvegetated (often incised) channels that have little contact with wetland vegetation, or through a zone of open water such as an instream pond or lake."},{"$f":"F!D110","v":0},0,{"$f":"D73*E73","v":0}]
[null,null,{"$f":"F!C111","v":"bumps into herbaceous vegetation but mostly remains in fairly straight channels."},{"$f":"F!D111","v":0},1,{"$f":"D74*E74","v":0}]
[null,null,{"$f":"F!C112","v":"bumps into herbaceous vegetation and mostly spreads throughout, or is in widely  meandering, multi-branched, or braided channels."},{"$f":"F!D112","v":0},2,{"$f":"D75*E75","v":0}]
[null,null,{"$f":"F!C113","v":"bumps into tree trunks and/or shrub stems but mostly remains in fairly straight channels."},{"$f":"F!D113","v":0},3,{"$f":"D76*E76","v":0}]
[null,null,{"$f":"F!C114","v":"bumps into tree trunks and/or shrub stems and follows a fairly indirect path from entrance to exit (meandering, multi-branched, or braided)"},{"$f":"F!D114","v":0},4,{"$f":"D77*E77","v":0}]
[{"$f":"F!A115","v":"F26"},{"$f":"F!B115","v":"Channel Connection & Outflow Duration"},{"$f":"F!C115","v":"The most persistent surface water connection (outlet channel or pipe, ditch, or overbank water exchange) between the AA and the closest off-site downslope water body is:"},null,null,null,{"$f":"IF((AllSat+AllSat1>0),\"\", MAX(F79:F83)/MAX(E79:E83))","v":0},"OutDura4","Wetlands that lack outlets retain or remove all nitrate that enters them. Wetlands that connect to downslope water bodies for only part of the year may export less nitrate annually than those with persistent outflow.  In calculations, is excluded automatically (cell goes blank) if wetland never has surface water during an average year."]
[null,null,{"$f":"F!C116","v":"persistent (>9 months/year, including times when frozen)"},{"$f":"F!D116","v":0},1,{"$f":"D79*E79","v":0}]
[null,null,{"$f":"F!C117","v":"seasonal (14 days to 9 months/year, not necessarily consecutive, including times when frozen)"},{"$f":"F!D117","v":0},2,{"$f":"D80*E80","v":0}]
[null,null,{"$f":"F!C118","v":"temporary (<14 days, not necessarily consecutive -- must be unfrozen)"},{"$f":"F!D118","v":0},3,{"$f":"D81*E81","v":0}]
[null,null,{"$f":"F!C119","v":"none -- but maps show a stream or other water body that is downslope from the AA and within a distance that is less than the AA's length.  If so, mark \"1\" here and SKIP TO F28 (Groundwater). "},{"$f":"F!D119","v":0},6,{"$f":"D82*E82","v":0}]
[null,null,{"$f":"F!C120","v":"no surface water flows out of the wetland except possibly during extreme events (<once per 10 years). Or, water flows only into a wetland, ditch, or lake that lacks an outlet.  If so, mark \"1\" here and SKIP TO F28 (Groundwater). "},{"$f":"F!D120","v":0},6,{"$f":"D83*E83","v":0}]
[{"$f":"F!A121","v":"F27"},{"$f":"F!B121","v":"Outflow Confinement"},{"$f":"F!C121","v":"During major runoff events, in the places where surface water exits the AA or connected waters nearby, it:"},null,null,null,{"$f":"IF((OutNone=1),\"\",MAX(F85:F87)/MAX(E85:E87))","v":0},"Constric4","Narrow outlets limit water outflow from a wetland and its downstream or downslope movement, thus causing water to back up into the wetland, which allows more time for nitrate to be processed. The types of outlets described here are ones that typically are more constricted than natural channels, which usually have adjusted over time to local runoff and thus are wider relative to volume of flow received.  In calculations, is excluded automatically (cell goes blank) if no outlet."]
[null,null,{"$f":"F!C122","v":"mostly passes through a pipe, culvert, narrowly breached dike, berm, beaver dam, or other partial obstruction (other than natural topography) that does not appear to drain the wetland artificially during most of the growing season."},{"$f":"F!D122","v":0},2,{"$f":"D85*E85","v":0}]
[null,null,{"$f":"F!C123","v":"leaves through natural exits (channels or diffuse outflow), not mainly through artificial or temporary features"},{"$f":"F!D123","v":0},1,{"$f":"D86*E86","v":0}]
[null,null,{"$f":"F!C124","v":"exported more quickly than usual due to ditches or pipes within the AA (or connected to its outlet or within 10 m of the AA's edge) which drain the wetland artificially, or water is pumped out of the AA."},{"$f":"F!D124","v":0},0,{"$f":"D87*E87","v":0}]
[{"$f":"F!A125","v":"F28"},{"$f":"F!B125","v":"Groundwater: Strength of Evidence"},{"$f":"F!C125","v":"Select first applicable choice. "},null,null,null,{"$f":"IF((D91=1),\"\",MAX(F89:F91)/MAX(E89:E91))","v":0},"Groundw4","Many studies have highlighted the importance of subsurface (hyporheic) flow, or groundwater discharge, to denitrification rates in both riverine (Clilverd et al. 2008) and non-riverine (e.g., Kroeger & Charette 2008) wetlands. However, in some areas groundwater is a significant source of nitrogen.  In calculations, is excluded automatically (cell goes blank) if no evidence of groundwater influx; otherwise is rated based on response in column D."]
[null,null,{"$f":"F!C126","v":"Groundwater monitoring has demonstrated that groundwater primarily discharges to the wetland for longer periods during the year than periods when the wetland recharges the groundwater.  Or, springs are known to be present within the AA.\n\n\n"},{"$f":"F!D126","v":0},3,{"$f":"D89*E89","v":0}]
[null,null,{"$f":"F!C127","v":"One or more of the following are true: (a) the upper end of the AA is located very close to the base of (but mostly not ON) a natural slope much steeper (usually >15%) than that within the AA and longer than 100 m, OR\n(b) rust deposits (\"iron floc\"), colored precipitates, or dispersible natural oil sheen are prevalent in the AA, OR\n(c) AA water is remarkably clear in contrast to naturally stained waters typical in nearby wetlands, OR\n(d) AA is located at a geologic fault.\n\n"},{"$f":"F!D127","v":0},2,{"$f":"D90*E90","v":0}]
[null,null,{"$f":"F!C128","v":"Neither of above is true, although some groundwater may discharge to or flow through the AA.  Or groundwater influx is unknown."},{"$f":"F!D128","v":0},0,{"$f":"D91*E91","v":0}]
[{"$f":"F!A129","v":"F29"},{"$f":"F!B129","v":"Internal Gradient"},{"$f":"F!C129","v":"The gradient along most of the flow path within the AA is:"},null,null,null,{"$f":"MAX(F93:F96)/MAX(E93:E96)","v":0},"Gradient4","Flatter wetlands are more likely than steep ones to slow runoff, facilitating more deposition of suspended matter and the nitrate that is associated with it, and also supporting anaerobic conditions that lead to more nitrate removal via denitrification. Steeper gradients in a wetland imply greater potential for outflow and transport downslope, and more aerobic conditions. "]
[null,null,{"$f":"F!C130","v":"<2%, or, no slope is ever apparent (i.e., flat). Or, the wetland is in a depression or pond with no inlet and no outlet."},{"$f":"F!D130","v":0},4,{"$f":"D93*E93","v":0}]
[null,null,{"$f":"F!C131","v":"2-5%"},{"$f":"F!D131","v":0},2,{"$f":"D94*E94","v":0}]
[null,null,{"$f":"F!C132","v":"6-10%"},{"$f":"F!D132","v":0},1,{"$f":"D95*E95","v":0}]
[null,null,{"$f":"F!C133","v":">10%"},{"$f":"F!D133","v":0},0,{"$f":"D96*E96","v":0}]
[{"$f":"F!A134","v":"F30"},{"$f":"F!B134","v":"Total Woody Cover -% of the Vegetated AA"},{"$f":"F!C134","v":"Within the entire vegetated part of the AA, the percentage occupied by trees or shrubs taller than 1 m is:"},null,null,null,{"$f":"MAX(F98:F102)/MAX(E98:E102)","v":0},"WoodyPct4","Tree roots can extend the subsurface zone of denitrification by oxidizing deeper subsurface areas, as well as retaining drifting snow which helps sustain soil moisture necessary for denitrification. Trees also take up and temporarily retain nitrate, as well as adding carbon to the soil, which promotes denitrification.  However, dense canopy cover reduces soil warming in spring (Hennon et al. 2010) which otherwise could accelerate denitrification."]
[null,null,{"$f":"F!C135","v":"<5% of the vegetated AA, or there is no woody vegetation in the AA.  SKIP to F38 (N Fixers)"},{"$f":"F!D135","v":0},0,{"$f":"D98*E98","v":0}]
[null,null,{"$f":"F!C136","v":"5-25%.  "},{"$f":"F!D136","v":0},1,{"$f":"D99*E99","v":0}]
[null,null,{"$f":"F!C137","v":"25-50%"},{"$f":"F!D137","v":0},2,{"$f":"D100*E100","v":0}]
[null,null,{"$f":"F!C138","v":"50-75%"},{"$f":"F!D138","v":0},3,{"$f":"D101*E101","v":0}]
[null,null,{"$f":"F!C139","v":">75%"},{"$f":"F!D139","v":0},4,{"$f":"D102*E102","v":0}]
[{"$f":"F!A194","v":"F41"},{"$f":"F!B194","v":"% Bare Ground & Thatch"},{"$f":"F!C194","v":"Consider the parts of the AA that lack surface water at the driest time of the growing season.  Viewed from directly above the ground layer, the predominant condition in those areas at that time is:"},null,null,null,{"$f":"MAX(F104:F107)/MAX(E104:E107)","v":0},"Gcover4","Dense vegetation offers frictional resistance to runoff, promoting deposition of organic nitrogen and resisting erosion. Vegetation takes up nitrate at least seasonally and plant roots can promote denitrification by providing a carbon source and oxidizing otherwise anoxic subsurface soils.  However, shade from plants reduces soil temperature which slows the denitrification rate (Hogg & Lieffers 1991), and emissions of harmful nitrous oxide can be greater in wetlands with denser vegetation."]
[null,null,{"$f":"F!C195","v":"Little or no (<5%) bare ground is visible between erect stems or under canopy anywhere in the vegetated AA. Ground is extensively blanketed by dense thatch, moss, lichens, graminoids with great stem densities, or plants with ground-hugging foliage. "},{"$f":"F!D195","v":0},3,{"$f":"D104*E104","v":0}]
[null,null,{"$f":"F!C196","v":"Slightly bare ground (5-20% bare between plants) is visible in places, but those areas comprise less than 5% of the unflooded parts of the AA."},{"$f":"F!D196","v":0},2,{"$f":"D105*E105","v":0}]
[null,null,{"$f":"F!C197","v":"Much bare ground (20-50% bare between plants) is visible in places, and those areas comprise more than 5% of the unflooded parts of the AA. "},{"$f":"F!D197","v":0},1,{"$f":"D106*E106","v":0}]
[null,null,{"$f":"F!C198","v":"Other conditions"},{"$f":"F!D198","v":0},0,{"$f":"D107*E107","v":0}]
[{"$f":"F!A200","v":"F42"},{"$f":"F!B200","v":"Ground Irregularity"},{"$f":"F!C200","v":"Consider the parts of the AA that lack surface water at some time of the year.  Excluding slash from logging, the number of small pits, raised mounds, hummocks, boulders, upturned trees, animal burrows, gullies, natural levees, wide soil cracks, and microdepressions is:"},null,null,null,{"$f":"MAX(F109:F111)/MAX(E109:E111)","v":0},"Girreg4","These features cumulatively decelerate runoff, thus allowing for more biological processing and deposition of nitrate-containing suspended sediments, although usually only to a minor degree. The presence of soil cracks implies a potential downward extension of the aerobic zone, interspersing it with anaerobic areas, which should lead to greater denitrification. Studies of wastewater treatment wetlands have shown greater nitrate removal where pockets of deeper water are interspersed with shallower areas (i.e., diverse microtopography)."]
[null,null,{"$f":"F!C201","v":"Few or none (minimal microtopography; <1% of that area) "},{"$f":"F!D201","v":0},0,{"$f":"D109*E109","v":0}]
[null,null,{"$f":"F!C202","v":"Intermediate"},{"$f":"F!D202","v":0},2,{"$f":"D110*E110","v":0}]
[null,null,{"$f":"F!C203","v":"Several (extensive micro-topography)"},{"$f":"F!D203","v":0},3,{"$f":"D111*E111","v":0}]
[{"$f":"F!A204","v":"F43"},{"$f":"F!B204","v":"Upland Inclusions"},{"$f":"F!C204","v":"Within the AA, inclusions of upland that individually are >100 sq.m. are:"},null,null,null,{"$f":"IF((D113=1),\"\", MAX(F113:F115)/MAX(E113:E115))","v":0},"Inclus4","Upland soils are normally aerobic, whereas wetland soils are often anaerobic. Maximum denitrification occurs at the interface of aerobic and anaerobic conditions. Thus, if inclusions of aerobic non-wetland soils are numerous and interspersed throughout a wetland, the extent of denitrification overall should be greater."]
[null,null,{"$f":"F!C205","v":"Few or none"},{"$f":"F!D205","v":0},0,{"$f":"D113*E113","v":0}]
[null,null,{"$f":"F!C206","v":"Intermediate (1 - 10% of vegetated part of the AA)."},{"$f":"F!D206","v":0},1,{"$f":"D114*E114","v":0}]
[null,null,{"$f":"F!C207","v":"Many (e.g., wetland-upland \"mosaic\", >10% of the vegetated AA)."},{"$f":"F!D207","v":0},2,{"$f":"D115*E115","v":0}]
[{"$f":"F!A208","v":"F44"},{"$f":"F!B208","v":"Soil Texture"},{"$f":"F!C208","v":"In parts of the AA that lack persistent water, the texture of soil in the uppermost layer is mostly:  [To determine this, use a trowel to check in at least 3 widely spaced locations, and use the soil texture key in Appendix A of the Manual]"},null,null,null,{"$f":"MAX(F117:F120)/MAX(E117:E120)","v":0},"SoilTex4","Denitrification rates are often limited by the amount of available carbon. Organic soils have the most carbon, and coarse soils usually have the least. Denitrification enzyme activity, on a per gram basis, is typically greater in organic soils than mineral soils (Van Hoewyk et al. 2000). However, the acidic nature of many organic soils can limit denitrification, the major process for nitrate removal. Soils having less than 65% silt and clay have very limited capacity to remove nitrate via denitrification (Pinay et al. 2003). Emissions of nitrous oxide (a detrimental greenhouse gas) are most likely to occur in soils that are poor in organic matter but rich in nitrogen (e.g., the carbon-nitrogen ratio is less than 25, Hunt et al. 2007). "]
[null,null,{"$f":"F!C209","v":"Loamy: includes loam, sandy loam"},{"$f":"F!D209","v":0},1,{"$f":"D117*E117","v":0}]
[null,null,{"$f":"F!C210","v":"Fines: includes silt, glacial flour, clay, clay loam, silty clay, silty clay loam, sandy clay, sandy clay loam."},{"$f":"F!D210","v":0},2,{"$f":"D118*E118","v":0}]
[null,null,{"$f":"F!C211","v":"Organic"},{"$f":"F!D211","v":0},3,{"$f":"D119*E119","v":0}]
[null,null,{"$f":"F!C212","v":"Coarse: includes sand, loamy sand, gravel, cobble, stones, boulders, fluvents, fluvaquents, riverwash."},{"$f":"F!D212","v":0},0,{"$f":"D120*E120","v":0}]
[{"$f":"F!A259","v":"F55"},{"$f":"F!B259","v":"New Wetland"},{"$f":"F!C259","v":"The AA is (or is within, or contains) a \"new\" wetland resulting from human actions (e.g., excavation, impoundment) or debris flows,  or other factors affecting what once was upland (non-hydric) soil."},null,null,null,{"$f":"IF((D127=1),\"\",MAX(F122:F126)/MAX(E122:E126))","v":0},"NewWet","Constructed (and some restored) wetlands typically have lower soil organic matter (Shaffer & Ernst 1999), and that deficit limits denitrification that otherwise removes nitrate. Thus, new wetlands would be expected to release the most nitrate to downstream waters. However, the proportion of incoming nitrate that is exported in some cases is greater in soils that are more fertile, i.e., nearing nitrate saturation, with a C:N ratio lower than 25 (e.g., Gundersen et al. 2006)."]
[null,null,{"$f":"F!C260","v":"No"},{"$f":"F!D260","v":0},5,{"$f":"D122*E122","v":0}]
[null,null,{"$f":"F!C261","v":"yes, and created 20 - 100 years ago "},{"$f":"F!D261","v":0},2,{"$f":"D123*E123","v":0}]
[null,null,{"$f":"F!C262","v":"yes, and created 3-20 years ago"},{"$f":"F!D262","v":0},1,{"$f":"D124*E124","v":0}]
[null,null,{"$f":"F!C263","v":"yes, and created within last 3 years"},{"$f":"F!D263","v":0},0,{"$f":"D125*E125","v":0}]
[null,null,{"$f":"F!C264","v":"yes, but time of origin unknown"},{"$f":"F!D264","v":0},1,{"$f":"D126*E126","v":0}]
[null,null,{"$f":"F!C265","v":"unknown if new within 20 years or not"},{"$f":"F!D265","v":0}]
[{"$f":"F!A323","v":"F68"},{"$f":"F!B323","v":"Wetland as a % of Its Contributing Area (Catchment)"},{"$f":"F!C323","v":"View the approximate boundaries of the wetland's catchment (CA) as shown in the map AESRD provides in response to your data request.  Then adjust those boundaries if necessary based on your field observations of the surrounding terrain, and/or by using procedures described in the ABWRET Manual. Relative to the extent of this catchment (but excluding the area of the AA), this AA and any bordering waters together comprise (select ONE):"},null,null,null,{"$f":"(MAX(F129:F132))/MAX(E129:E132)","v":0},"WetPctCA4","Where a wetland comprises a large proportion of its catchment, nutrient loading is more likely to occur at rates and levels that can be processed effectively."]
[null,null,{"$f":"F!C324","v":"<1% of their catchment"},{"$f":"F!D324","v":0},0,{"$f":"D129*E129","v":0}]
[null,null,{"$f":"F!C325","v":"1 to 10% of their catchment"},{"$f":"F!D325","v":0},1,{"$f":"D130*E130","v":0}]
[null,null,{"$f":"F!C326","v":"10 to 100%  of their catchment"},{"$f":"F!D326","v":0},2,{"$f":"D131*E131","v":0}]
[null,null,{"$f":"F!C327","v":"Larger than the area of their catchment (wetland has essentially no catchment, e.g., isolated by dikes with no input channels, or is a raised bog). "},{"$f":"F!D327","v":0},3,{"$f":"D132*E132","v":0}]
[{"$f":"S!A64","v":"S9"},{"$f":"S!B64","v":"Soil or Sediment Alteration Within the Assessment Area"},{"$f":"S!E81","v":"Stressor Subscore="},{"$f":"S!F81","v":0},null,null,{"$f":"IF((D133=0),\"\",1-(D133/5))","v":""},"SoilDisturb4","Soil compaction seals up pores in the soil that serve as habitat space for denitrifying bacteria, as well as causing a larger proportion of the precipitation to leave as runoff rather than infiltrate into subsurface areas where denitrification is greatest. Soil erosion often results in loss of carbon-rich upper soil layers that are important to denitrification."]
[]
[null,null,"Denitrification: Temperature Control [Temp]"]
[null,"Wetlands <10 hectares:","AVERAGE(1-Sub0Days, GrowDD, Aspect, WoodyPct4, Gcover4)",null,null,null,{"$f":"IF((GT10HA=1),G137,IFERROR(AVERAGE(GrowDD, 1-Sub0Days, Aspect, WoodyPct4, Gcover4),\"\"))","v":0.33333333333333331}]
[null,"Wetlands >10 hectares:","Substituted WetWooded.",null,null,null,{"$f":"IFERROR(AVERAGE(GrowDD, 1-Sub0Days, Aspect, WetWooded, Gcover4),\"\")","v":0.5}]
[]
[null,null,"Denitrification: Labile Carbon Control [Carb]"]
[null,"Wetlands <10 hectares:","AVERAGE(SoilTex4, SoilOrgPct, SoilDisturb4, OWpct4, Wettype4, NewWet)",null,null,null,{"$f":"IF((GT10HA=1),G141,IFERROR(AVERAGE(SoilTex4, SoilOrgPct, SoilDisturb4, WetVegArea, OWpct4, Wettype4, NewWet),\"\"))","v":0}]
[null,"Wetlands >10 hectares:","Substituted: SoilTex, 1-OWpct",null,null,null,{"$f":"IFERROR(AVERAGE(SoilTex_NROE, SoilOrgPct, SoilDisturb4, WetVegArea, 1-OWpct, Wettype4, NewWet),\"\")","v":0.33333333333333331}]
[]
[null,null,"Nitrification- Denitrification:  Redox [Redox]"]
[null,"Wetlands <10 hectares:","AVERAGE(1-WatProb, WetPerim2Area, SwampMarshPct, Interspers4,  Inclus4, Groundw4, PermWpct4, SatPct4, SeasWpct4, Fluctu4) ",null,null,null,{"$f":"IF((GT10HA=1),G145, IFERROR(AVERAGE(1-WatProb, WetPerim2Area, SwampMarshPct, Interspers4,Inclus4,Groundw4, PermWpct4, SatPct4, SeasWpct4, Fluctu4),\"\"))","v":0.125}]
[null,"Wetlands >10 hectares:","Substituted MixWaterVeg",null,null,null,{"$f":"IFERROR(AVERAGE(1-WatProb, WetPerim2Area, SwampMarshPct, MixWaterVeg,Groundw4, Inclus4, PermWpct4, SatPct4, SeasWpct4, Fluctu4),\"\")","v":0.14285714285714285}]
[]
[null,null,"Processing Time [Delay]"]
[null,"Wetlands <10 hectares:","AVERAGE(WetPctCA4, PondPct4, Gradient4, Thruflo4, Girreg4, Constric4, VwidthAbs4) ",null,null,null,{"$f":"IF((GT10HA=1),G149, IFERROR(AVERAGE(WetPctCA4, Gradient4, PondPct4,  ThruFlo4, Girreg4, Constric4, VwidthAbs4),\"\"))","v":0}]
[null,"Wetlands >10 hectares:","Added LGindex",null,null,null,{"$f":"IFERROR(AVERAGE(WetPctCA4, LGIndex, Gradient4, PondPct4,  ThruFlo4, Girreg4, Constric4, VwidthAbs4),\"\")","v":0}]
[]
[null,null,"Export [OUT]"]
[null,null,"OutDura4",null,null,null,{"$f":"OutDura4","v":0}]
[]
[null,null,"ABWRET-A FUNCTION MODEL"]
[null,null,"Nitrogen Removal"]
[null,null,"IF((OutNone + OutNone1>0),10, ELSE: AVERAGE(TEMP, CARB, REDOX, DELAY, OUT)",null,null,null,{"$f":"IF((OutNone + OutNone1>0),10, 10*AVERAGE(TEMP1A, CARB1A, REDOX1A, DELAY1A, OutDura4))","v":0.91666666666666663}]
[null,null,null,null,null,null,null,null,"Literature Cited"]
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[null,1,"IF(ChannConn + RipFloodPl = 0), then =10",null,null,null,null,null,"Anderson, K. A. and J. A. Downing. 2006. Dry and wet atmospheric deposition of nitrogen, phosphorus and silicon in an agricultural region. Water Air and Soil Pollution 176:351-374."]
[null,2,"ELSE calculate these averages:",null,null,null,null,null,"Bayley, S. E. and R. L. Mewhort. 2004. Plant community structure and junctional differences between marshes and fens in the southern boreal region of Alberta, Canada. Wetlands 24:277-294."]
[null,"a.","AVERAGE(1-Sub0Days, GrowDD)",{"$f":"IFERROR(AVERAGE(1-Sub0Days, GrowDD),\"\")","v":1},null,null,null,null,"Bedford, B. L., M. R. Walbridge, and A. Aldous. 1999. Patterns in nutrient availability and plant diversity of temperate North American wetlands. Ecology 80:2151-2169."]
[null,"b.","AVERAGE(Aspect,WetWooded)",{"$f":"IFERROR(AVERAGE(Aspect,WetWooded),\"\")","v":""},null,null,null,null,"Berendse, F., N. Van Breemen, H. Rydin, A. Buttler, M. Heijmans, M. Hoosbeek, J. A. H. Lee, E. Mitchell, T. Saarinen, H. Vasander, and B. Wallén. 2001. Raised atmospheric CO2 levels and increased N deposition cause shifts in plant species composition and production in Sphagnum bogs. Global Change Biology 7."]
[null,"c.","AVERAGE(a, b)",{"$f":"IFERROR(AVERAGE(D161,D162),\"\")","v":1},null,null,null,null,"Blevins, L., C. Prescott, and A. Van Niejenhuis. 2006. The roles of nitrogen and phosphorus in increasing productivity of western hemlock and western redcedar plantations on northern Vancouver Island. Forest Ecology and Management 234:116-122."]
[null,"d.","AVERAGE(SoilTex, SoilOrgPct)",{"$f":"IFERROR(AVERAGE(SoilTex, SoilOrgPct),\"\")","v":""},null,null,null,null,"Bragazza, L., T. Tahvanainen, L. Kutnar, H. Rydin, J. Limpens, M. Hájek, P. Grosvernier, T. Hájek, P. Hajkova, I. Hansen, P. Iacumin, and R. Gerdol. 2004. Nutritional constraints in ombrotrophic Sphagnum plants under increasing atmospheric nitrogen deposition in Europe. New Phytologist 163."]
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[null,3,"10*AVERAGE(WatProb, SwampMarshPct, WetPerim2Area, MixWaterVeg, c, d, e)",{"$f":"10*AVERAGE(WatProb, SwampMarshPct, WetPerim2Area, MixWaterVeg, D163, D164, D165)","v":10},null,null,null,null,"Cooke, S. E. and E. E. Prepas. 1998. Stream phosphorus and nitrogen export from agricultural and forested watersheds on the Boreal Plain. Canadian Journal of Fisheries and Aquatic Sciences 55:2292-2299."]
[null,null,null,null,null,null,null,null,"Cortini, F. and P. G. Comeau. 2008. Effects of red alder and paper birch competition on juvenile growth of three conifer species in southwestern British Columbia. Forest Ecology and Management 256:1795-1803."]
[null,null,"ABWRET-E with substitutions:",null,null,null,null,null,"D’Amore, D. V., P. E. Hennon, P. G. Schaberg, and G. J. Hawley. 2009. Adaptation to exploit nitrate in surface soils predisposes yellow-cedar to climate-induced decline while enhancing the survival of western redcedar: A new hypothesis. Forest Ecology and Management 258:2261-2268."]
[null,1,"IF(OutNone+OutNone1>0), then =10",null,null,null,null,null,"D’Amore, A., V. Hemingway, and K. Wasson. 2010. Do a threatened native amphibian and its invasive congener differ in response to human alteration of the landscape? Biological Invasions 12:145-154."]
[null,2,"ELSE calculate these averages:",null,null,null,null,null,"Dillaha, T. A., R. B. Reneau, S. Mostaghimi, and D. Lee. 1989. Vegetative filter strips for agricultural nonpoint source pollution-control. Transactions of the  ASAE 32:513-519."]
[null,"a.","AVERAGE(1-Sub0Days, GrowDD)",{"$f":"IFERROR(AVERAGE(1-Sub0Days, GrowDD),\"\")","v":1},null,null,null,null,"Dillaha, T. A., J. H. Sherrard, D. Lee, S. Mostaghimi, and V. O. Shanholtz. 1988. Evaluation of vegetative filter strips as a best management practice for feed lots. Journal Water Pollution Control Federation 60:1231-1238."]
[null,"b.","AVERAGE(Aspect,WetWooded)",{"$f":"IFERROR(AVERAGE(Aspect,WetWooded),\"\")","v":""},null,null,null,null,"Dosskey, M. G. 2001. Toward quantifying water pollution abatement in response to installing buffers on crop land. Environmental Management 28:577-598."]
[null,"c.","AVERAGE(a, b)",{"$f":"IFERROR(AVERAGE(D171,D172),\"\")","v":1},null,null,null,null,"Fellman, J. B. and D. V. D'Amore. 2007. Nitrogen and phosphorus mineralization in three wetland types in Southeast Alaska, USA. Wetlands 27:44-53."]
[null,"d.","AVERAGE(SoilTex4, SoilOrgPct)",{"$f":"IFERROR(AVERAGE(SoilTex, SoilOrgPct),\"\")","v":""},null,null,null,null,"Gunderson, L. H., S. R. Carpenter, C. Folke, P. Olsson, and G. D. Peterson. 2006. Water RATs (resilience, adaptability, and transformability) in lake and wetland social-ecological systems. Ecology and Society 11:16."]
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[null,null,null,null,null,null,null,null,"King, R. S., M. E. Baker, D. F. Whigham, D. E. Weller, T. E. Jordan, P. F. Kazyak, and M. K. Hurd. 2005. Spatial considerations for linking watershed land cover to ecological indicators in streams. Ecological Applications 15:137-153."]
[null,null,null,null,null,null,null,null,"Knox, A. K., R. A. Dahgren, K. W. Tate, and E. R. Atwill. 2008. Efficacy of natural wetlands to retain nutrient, sediment and microbial pollutants. Journal of Environmental Quality 37:1837-1846."]
[null,null,null,null,null,null,null,null,"Kroeger, K. D. and M. A. Charette. 2008. Nitrogen biogeochemistry of submarine groundwater discharge. Limnology and Oceanography 53:1025-1079."]
[null,null,null,null,null,null,null,null,"Lertzman, K. P., G. D. Sutherland, A. Inselberg, and S. C. Saunders. 1996. Canopy gaps and the landscape mosaic in a coastal temperate rain forest. Ecology 77:1254-1270."]
[null,null,null,null,null,null,null,null,"Li, Y. and D. H. Vitt. 1997. Patterns of retention and utilization of aerially deposited nitrogen in boreal peatlands. Ecoscience. Sainte-Foy 4:106-116."]
[null,null,null,null,null,null,null,null,"Madden, S. S., G. R. Robinson, and J. G. Arnason. 2007. Spatial variation in stream water quality in relation to riparian buffer dimensions in a rural watershed of eastern New York state. Northeastern Naturalist 14:605-618."]
[null,null,null,null,null,null,null,null,"Mayers, P. M., S. K. Reynolds, M. D. McCutchen, and T. J. Canfield. 2005. Riparian Buffer Width, Vegetative Cover, and Nitrogen Removal Effectiveness: A Review of Current Science and Regulations, EPA/600/R-05/118. USEPA, Office of Research and Development, Washington, DC."]
[null,null,null,null,null,null,null,null,"Mayer, P. M., S. K. Reynolds, Jr., M. D. McCutchen, and T. J. Canfield. 2007. Meta-analysis of nitrogen removal in riparian buffers. Journal of Environmental Quality 36:1172-1180."]
[null,null,null,null,null,null,null,null,"McBride, M. and D. B. Booth. 2005. Urban impacts on physical stream condition: Effects of spatial scale, connectivity, and longitudinal trends. Journal of the American Water Resources Association 41:565-580."]
[null,null,null,null,null,null,null,null,"McDonald, M. A., B. J. Hawkins, C. E. Prescott, and J. Kimmins, P. 1994. Growth and foliar nutrition of western red cedar fertilized with sewage-sludge, pulp sludge, fish silage and wood ash on northern Vancouver Island. Canadian Journal of Forest Research 24:297-301."]
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[null,null,null,null,null,null,null,null,"Shaffer, P. W. and T. L. Ernst. 1999. Distribution of soil organic matter in freshwater emergent/open water wetlands in the Portland, Oregon metropolitan area. Wetlands 19:505-516."]
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[null,null,null,null,null,null,null,null,"Van Hoewyk, D., P. M. Groffman, E. Kiviat, G. Mihocko, and G. Stevens. 2000. Soil nitrogen dynamics in organic and mineral soil calcareous wetlands in eastern New York. Soil Science Society of America Journal 64: 2168–2173."]
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{"sheet":"OE","index":15,"n_rows":146,"n_cols":9,"rows_kept":146,"cut":false,"hidden":false,"merged":[[110,1,116,1],[110,0,116,0],[105,0,109,0],[100,0,104,0],[88,0,93,0],[105,1,109,1],[100,1,104,1],[94,1,99,1],[88,1,93,1],[132,2,132,3],[18,7,23,7],[13,7,17,7],[110,8,116,8],[100,8,104,8],[67,8,72,8],[24,8,29,8],[88,8,93,8],[77,8,81,8],[105,8,109,8],[94,8,99,8],[82,8,87,8],[0,4,0,7],[18,0,23,0],[94,0,99,0],[110,7,116,7],[105,7,109,7],[100,7,104,7],[94,7,99,7],[88,7,93,7],[82,7,87,7],[77,7,81,7],[73,7,76,7],[67,7,72,7],[61,7,66,7],[56,7,59,7],[43,7,49,7],[35,7,42,7],[73,1,76,1],[43,0,49,0],[82,0,87,0],[77,1,81,1],[77,0,81,0],[73,0,76,0],[61,1,66,1],[56,0,59,0],[82,1,87,1],[24,1,29,1],[30,8,34,8],[50,8,55,8],[30,0,34,0],[30,1,34,1],[50,1,55,1],[50,0,55,0],[50,7,55,7],[30,7,34,7],[24,7,29,7],[35,8,42,8],[43,1,49,1],[0,0,0,1],[73,8,76,8],[61,8,66,8],[35,0,42,0],[35,1,42,1],[43,8,49,8],[67,0,72,0],[67,1,72,1],[56,8,59,8],[61,0,66,0],[56,1,59,1],[13,8,17,8],[18,8,23,8],[13,1,17,1],[18,1,23,1],[24,0,29,0]]}
["Organic                          Matter                                      Export",null,"The effectiveness for producing and subsequently exporting organic matter, either particulate or dissolved, along with associated compounds and elements such as iron.\n","OE",null,null,null,null,"The model does not address the ecological need for organic nutrients in the receiving stream or lake at a particular location.  At some locations nutrients may limit aquatic productivity while at others additional nutrients could cause problems associated with overenrichment.  Also, the model is unable to differentiate among the various forms of organic nutrients, e.g., carbon that is easily consumed and cycled vs. carbon that provides less nutrition and cycles slowly in food webs. The model does not address the potential export of organic nutrients via insect emergence and wetland animal movements. "]
["#","Function Indicators from Estimator","Scoring Notes",null,null,null,"Normalised Score","Indicator Abbreviation or Formula","Rationale"]
[{"$f":"OF!A5","v":"OF4"},{"$f":"OF!C5","v":"Channel Connection"},null,null,null,null,{"$f":"IF((ChannConn=\"\"),\"\",ChannConn)","v":""},"ChannConn","Annual export of accumulated organic matter to downslope water bodies is greater in wetlands with outlets, especially those with persistent outflow (Pacific et al. 2010).  Nonetheless, even wetlands that lack outlets may export variable amounts of dissolved carbon via subsurface infiltration and \"pipes\" created by decayed subsurface peat and tree roots which cannot be evaluated in a rapid assessment."]
[{"$f":"OF!A13","v":"OF12"},{"$f":"OF!C13","v":"% of the Wetland that is Fen Bog or Marsh"},null,null,null,null,{"$f":"IF((FenBogMarsh=\"\"),\"\",FenBogMarsh)","v":""},"FenBogMarsh","These wetland classes usually have the largest stores of carbon and other nutrients available for downstream export."]
[{"$f":"OF!A18","v":"OF17"},{"$f":"OF!C18","v":"Growing Degree Days"},null,null,null,null,{"$f":"IF((GrowDD=\"\"),\"\",GrowDD)","v":""},"GrowDD","Plants are most productive at warmer soil or sediment temperatures, and their foliage that contributes organic matter to downslope food chains decomposes most rapidly under warmer conditions (Fissore et al. 2009). Those conditions are described by increasing mean annual temperature. As soil temperatures increase, so does the concentration of DOC in forested wetland soils and streams, and in that form carbon is readily exported (D’Amore et al. 2010). The production of Sphagnum moss, a dominant species in many bogs and slope wetlands, is greater in warmer areas (Gunnarsson 2005)."]
[{"$f":"OF!A23","v":"OF22"},{"$f":"OF!C23","v":"L/G Index (Residence Time)"},null,null,null,null,{"$f":"IF((LGIndex=\"\"),\"\",LGIndex)","v":""},"LGIndex","Longer flow paths allow for more interaction between runoff and wetland vegetation, which potentially leads to removal and export of more decomposed organic matter."]
[{"$f":"OF!A28","v":"OF27"},{"$f":"OF!C28","v":"Interspersion Index for Internal Water & Vegetation (macroscale)"},null,null,null,null,{"$f":"IF((MixWaterVeg=\"\"),\"\",MixWaterVeg)","v":""},"MixWaterVeg","Interspersion of open water with vegetation would seem to promote greater export of organic matter from the vegetation or accumulated organic soils."]
[{"$f":"OF!A31","v":"OF30"},{"$f":"OF!C31","v":"% of AA that is Open Water (macro scale)"},"Inverse",null,null,null,{"$f":"IF((OWpct=\"\"),\"\",1-OWpct)","v":""},"OWpct","The probability that organic matter from wetland plants will be exported increases in relation to the percent of the inundated area containing such plants, provided some outflow paths exist."]
[{"$f":"OF!A43","v":"OF42"},{"$f":"OF!C43","v":"Riparian or Floodway Location"},null,null,null,null,{"$f":"IF((RipFloodpl=\"\"),\"\",RipFloodpl)","v":""},"RipFloodpl","Wetlands along streams or rivers or in floodplains are more likely to be exposed to moving water that can export organic matter downstream. "]
[{"$f":"OF!A47","v":"OF46"},{"$f":"OF!C47","v":"Organic Soil Content (macroscale)"},null,null,null,null,{"$f":"IF((SoilOrgPct=\"\"),\"\",SoilOrgPct)","v":""},"SoilOrgPct","Soil organic matter and the nutrients it contains are important to aquatic food chains."]
[{"$f":"OF!A50","v":"OF49"},{"$f":"OF!C50","v":"Soil Texture (macroscale)"},"See Table 3 worksheet.",null,null,null,{"$f":"IF((SoilTex_NROE=\"\"),\"\",SoilTex_NROE)","v":""},"SoilTex_NROE","See above."]
[{"$f":"OF!A69","v":"OF68"},{"$f":"OF!C69","v":"Wetland Vegetated Area"},null,null,null,null,{"$f":"IF((WetVegArea=\"\"),\"\",WetVegArea)","v":""},"WetVegArea","Wetland vegetation is a primary source of the organic matter that is subject to export from wetlands."]
["#","Function Indicators from Onsite Visit","Categorical Choices","Data","Weight","Data  x  Weight","Normalised Score","Indicator Abbreviation or Formula","Rationale & Scoring Notes"]
[{"$f":"F!A6","v":"F1"},{"$f":"F!B6","v":"Wetland Type - Predominant"},{"$f":"F!C6","v":"Most of the vegetated part of the AA (wetland Assessment Area) is a (select ONE):"},null,null,null,{"$f":"MAX(F15:F18)/MAX(E15:E18)","v":0},"Wettype6","Carbon from marshes and fens is often more biodegradable (and thus more exportable and valuable to food chains over a wider area) than bog and forested wetland carbon (D’Amore et al. 2010). The same may be true of riparian shrub/forest wetlands, and their connectivity to other water bodies is usually greater, potentially leading to greater export.  Bogs usually have the largest amounts of carbon in storage (as peat), and also tend to fix carbon more readily than more fertile wetlands (fens) (Glenn et al. 2006), but connectivity to other water bodies is generally less than other wetland types."]
[{"$f":"F!A7","v":"F1.1"},null,{"$f":"F!C7","v":"Wooded Swamp"},{"$f":"F!D7","v":0},2,{"$f":"D15*E15","v":0}]
[{"$f":"F!A8","v":"F1.2"},null,{"$f":"F!C8","v":"Bog"},{"$f":"F!D8","v":0},1,{"$f":"D16*E16","v":0}]
[{"$f":"F!A9","v":"F1.3"},null,{"$f":"F!C9","v":"Fen"},{"$f":"F!D9","v":0},5,{"$f":"D17*E17","v":0}]
[{"$f":"F!A10","v":"F1.4"},null,{"$f":"F!C10","v":"Marsh or Shallow Open Water"},{"$f":"F!D10","v":0},4,{"$f":"D18*E18","v":0}]
[{"$f":"F!A31","v":"F5"},{"$f":"F!B31","v":"% of Summertime Water That Is Shaded"},{"$f":"F!C31","v":"At mid-day during the warmest time of year, the area of surface water within the AA that is shaded (by emergent or woody vegetation, incised channels, streambanks, or other features also present within the AA) is:"},null,null,null,{"$f":"IF((NoPersis=1),\"\",MAX(F20:F24)/MAX(E20:E24))","v":0},"Shade6","Although shade can limit aquatic productivity and thus the amount of carbon subject to export, this indicator more importantly describes the proximity of vegetation to water, and thus the potential for detritus to be exported. In calculations, is excluded automatically (cell goes blank) if wetland never has surface water during an average year or if water is present only seasonally."]
[null,null,{"$f":"F!C32","v":"<5% of the water is shaded, or no surface water is present then."},{"$f":"F!D32","v":0},0,{"$f":"D20*E20","v":0}]
[null,null,{"$f":"F!C33","v":"5-25% of the water is shaded"},{"$f":"F!D33","v":0},1,{"$f":"D21*E21","v":0}]
[null,null,{"$f":"F!C34","v":"25-50% of the water is shaded"},{"$f":"F!D34","v":0},2,{"$f":"D22*E22","v":0}]
[null,null,{"$f":"F!C35","v":"50-75% of the water is shaded"},{"$f":"F!D35","v":0},3,{"$f":"D23*E23","v":0}]
[null,null,{"$f":"F!C36","v":">75% of the water is shaded"},{"$f":"F!D36","v":0},4,{"$f":"D24*E24","v":0}]
[{"$f":"F!A39","v":"F8"},{"$f":"F!B39","v":"% Flooded Only Seasonally"},{"$f":"F!C39","v":"The percentage of the AA that is covered by surface water only during the wettest time of year (and for >2 consecutive days during that time) is:"},null,null,null,{"$f":"IF((AllSat+AllSat1>0),\"\", MAX(F26:F30)/MAX(E26:E30))","v":0},"SeasWpct6","Prolonged inundation can stifle plant productivity, whereas seasonal inundation encourages it, and is often associated with conditions that contribute to the export of organic matter, e.g., river floods. Seasonally high water levels promote decomposition (Bayley & Mewhort, 2004) and thus facilitate the export of carbon. In calculations, is excluded automatically (cell goes blank) if wetland never has surface water during an average year."]
[null,null,{"$f":"F!C40","v":"<1%. "},{"$f":"F!D40","v":0},0,{"$f":"D26*E26","v":0}]
[null,null,{"$f":"F!C41","v":"1-25% "},{"$f":"F!D41","v":0},1,{"$f":"D27*E27","v":0}]
[null,null,{"$f":"F!C42","v":"25-50% "},{"$f":"F!D42","v":0},2,{"$f":"D28*E28","v":0}]
[null,null,{"$f":"F!C43","v":"50-95% "},{"$f":"F!D43","v":0},3,{"$f":"D29*E29","v":0}]
[null,null,{"$f":"F!C44","v":">95% "},{"$f":"F!D44","v":0},4,{"$f":"D30*E30","v":0}]
[{"$f":"F!A45","v":"F9"},{"$f":"F!B45","v":"Annual Water Fluctuation Range"},{"$f":"F!C45","v":"The annual fluctuation in surface water level within most of the parts of the AA that contain surface water is:"},null,null,null,{"$f":"IF((AllSat+AllSat1>0),\"\", IF((NoSeasonal=1),\"\",MAX(F32:F35)/MAX(E32:E35)))","v":0},"Fluctu6","Dynamic water levels in wetlands with outlets usually imply more productive wetlands and greater export of organic matter, whereas stable water levels typically imply less export. However, if water level fluctuations are too severe (e.g., greater than plant height) production of organic matter can diminish. In calculations, is excluded automatically (cell goes blank) if wetland never has surface water during an average year, or if none of it floods only seasonally."]
[null,null,{"$f":"F!C46","v":"<10 cm change (stable) "},{"$f":"F!D46","v":0},0,{"$f":"D32*E32","v":0}]
[null,null,{"$f":"F!C47","v":"10 cm - 50 cm change"},{"$f":"F!D47","v":0},1,{"$f":"D33*E33","v":0}]
[null,null,{"$f":"F!C49","v":"1-2 m change"},{"$f":"F!D49","v":0},2,{"$f":"D34*E34","v":0}]
[null,null,{"$f":"F!C50","v":">2 m change"},{"$f":"F!D50","v":0},3,{"$f":"D35*E35","v":0}]
[{"$f":"F!A62","v":"F12"},{"$f":"F!B62","v":"% of Water Ponded vs. Flowing "},{"$f":"F!C62","v":"The percentage of the AA's surface water that is ponded (stagnant, or flows so slowly that fine sediment is not held in suspension) during most of the time it is present, and which is either open or shaded by emergent vegetation is:"},null,null,null,{"$f":"IF((AllSat=1),\"\", IF((SmallAA=1),\"\", MAX(F37:F43)/MAX(E37:E43)))","v":0},"PondedPct6","Flowing rather than ponded waters provide the most opportunity for organic matter to be exported from wetlands.  In boreal regions, flowing waters also tend to be more productive. In calculations, is excluded automatically (cell goes blank) if wetland never has surface water during an average year. Also is excluded automatically if wetland is <0.01 ha."]
[null,null,{"$f":"F!C63","v":"<1% or none, or occupies <0.01 hectare cumulatively.  Nearly all water is flowing.  Enter \"1\" and SKIP to F21 (Stained Surface Water)."},{"$f":"F!D63","v":0},5,{"$f":"D37*E37","v":0}]
[null,null,{"$f":"F!C64","v":"1-5% of the water, and mainly in small pools.  The rest is flowing."},{"$f":"F!D64","v":0},4,0]
[null,null,{"$f":"F!C65","v":"1-5% of the water, and mainly in a single large pool or pond.  The rest is flowing."},{"$f":"F!D65","v":0},4,0]
[null,null,{"$f":"F!C66","v":"5-30% of the water"},{"$f":"F!D66","v":0},3,0]
[null,null,{"$f":"F!C67","v":"30-70% of the water"},{"$f":"F!D67","v":0},2,0]
[null,null,{"$f":"F!C68","v":"70-95% of the water"},{"$f":"F!D68","v":0},1,0]
[null,null,{"$f":"F!C69","v":">95% of the water.  Little or no visibly flowing water within the AA."},{"$f":"F!D69","v":0},0,0]
[{"$f":"F!A71","v":"F14"},{"$f":"F!B71","v":"% of Ponded Water That Is Open "},{"$f":"F!C71","v":"In ducks-eye aerial view, the percentage of the ponded water that is open (lacking emergent vegetation during most of the growing season, and unhidden by a forest or shrub canopy) is:"},null,null,null,{"$f":"IF((AllSat+AllSat>0),\"\",IF((NoPonded=1),\"\", IF((SmallAA=1),\"\", MAX(F45:F50)/MAX(E45:E50))))","v":0},"OWpct6","The probability that organic matter from wetland plants will be exported increases in relation to the percent of the inundated area containing such plants, provided some outflow paths exist. In calculations, is excluded automatically (cell goes blank) if wetland never has surface water during an average year. Also is excluded automatically if wetland has no ponded water or is <0.01 ha."]
[null,null,{"$f":"F!C72","v":"<1% or none, or largest pool occupies <0.01 hectares.  Enter \"1\" and SKIP to F20 (Floating Algae & Duckweed)."},{"$f":"F!D72","v":0},6,{"$f":"D45*E45","v":0}]
[null,null,{"$f":"F!C73","v":"1-5% of the ponded water.  Enter \"1\" and SKIP to F20."},{"$f":"F!D73","v":0},5,0]
[null,null,{"$f":"F!C74","v":"5-30% of the ponded water."},{"$f":"F!D74","v":0},4,0]
[null,null,{"$f":"F!C75","v":"30-70% of the ponded water."},{"$f":"F!D75","v":0},3,0]
[null,null,{"$f":"F!C76","v":"70-99% of the ponded water."},{"$f":"F!D76","v":0},2,0]
[null,null,{"$f":"F!C77","v":"100% of the ponded water. "},{"$f":"F!D77","v":0},1,0]
[{"$f":"F!A84","v":"F16"},{"$f":"F!B84","v":"Predominant Width of Vegetated Zone within Wetland"},{"$f":"F!C84","v":"At the driest time of year (or lowest water level), the average width of vegetated area in the AA that separates adjoining uplands from open water within the AA is:"},null,null,null,{"$f":"IF((AllSat+AllSat>0),\"\",IF((OpenW=0),\"\", IF((SmallAA=1),\"\", MAX(F52:F56)/MAX(E52:E56))))","v":""},"VwidthAbs6","The plant material from narrower (fringe) wetlands is often more vulnerable to transport into adjoining waters. However, wider wetlands represent larger total stores of organic matter available for waterborne export downstream or offsite, and export can occur during infrequent but extreme floods (Pacific et al. 2010). In calculations, is excluded automatically (cell goes blank) if wetland never has surface water during an average year. Also is excluded automatically if wetland lacks open water or is <0.01 ha."]
[null,null,{"$f":"F!C85","v":"<1 m"},{"$f":"F!D85","v":0},4,{"$f":"D52*E52","v":0}]
[null,null,{"$f":"F!C86","v":"1 - 9 m"},{"$f":"F!D86","v":0},3,{"$f":"D53*E53","v":0}]
[null,null,{"$f":"F!C87","v":"10 - 29 m"},{"$f":"F!D87","v":0},2,{"$f":"D54*E54","v":0}]
[null,null,{"$f":"F!C88","v":"30 - 49 m"},{"$f":"F!D88","v":0},1,{"$f":"D55*E55","v":0}]
[null,null,{"$f":"F!C90","v":"> 100 m"},{"$f":"F!D90","v":0},0,{"$f":"D56*E56","v":0}]
[{"$f":"F!A95","v":"F18"},{"$f":"F!B95","v":"Interspersion of Robust Emergents & Open Water"},{"$f":"F!C95","v":"During most of the growing season, the spatial pattern of tall robust herbaceous vegetation (e.g., cattail, bulrush) that has surface water beneath it is mostly:"},null,null,null,{"$f":"IF((AllSat+AllSat>0),\"\",IF((NoPonded=1),\"\",IF((NoOpenPonded+NoOpenPonded1>0),\"\",IF((AllOpenPond=1),\"\", IF((SmallAA=1),\"\", MAX(F58:F60)/MAX(E58:E60))))))","v":0},"Interspers6","Interspersion of open water with vegetation would seem to promote greater export of organic matter from the vegetation or accumulated organic soils. In calculations, is excluded automatically (cell goes blank) if wetland never has surface water during an average year, if no ponded water, if ponded water but no vegetation, if ponded but no open water, or if <0.01 ha."]
[null,null,{"$f":"F!C96","v":"Scattered in small clumps, islands, or patches throughout the surface water area."},{"$f":"F!D96","v":0},2,0]
[null,null,{"$f":"F!C97","v":"Intermediate"},{"$f":"F!D97","v":0},1,0]
[null,null,{"$f":"F!C98","v":"Clumped at one or a few sides of the surface water area, or mostly surrounds a central area of open water.  Or such vegetation is absent or covers <9 sq m and <1% of the AA."},{"$f":"F!D98","v":0},0,0]
[{"$f":"F!A101","v":"F21"},{"$f":"F!B101","v":"Stained Surface Water"},{"$f":"F!C101","v":"Most surface water is tea-colored (from tannins, not iron bacteria or silt), and/or its pH is usually <5.5. Nearby vegetation is mostly moss and/or conifers. "},{"$f":"F!D101","v":0},null,null,{"$f":"IF((AllSat+AllSat>0),\"\", IF((SmallAA=1),\"\", IF((D61=0),\"\",1)))","v":""},"Stained6","Stained water is direct evidence that dissolved organic matter is present. In calculations, is excluded automatically (cell goes blank) if condition is absent (0), or if wetland never has surface water during an average year, or if wetland is <0.01 ha.  "]
[{"$f":"F!A109","v":"F25"},{"$f":"F!B109","v":"Through Flow Pattern"},{"$f":"F!C109","v":"During its travel through the AA at the time of peak annual flow, most of the water arriving in channels [select only the ONE encountered by most of the incoming water]:"},null,null,null,{"$f":"IF((AllSat+AllSat>0),\"\", IF((Inflows=0),\"\",MAX(F63:F67)/MAX(E63:E67)))","v":""},"ThruFlo6","Increased channel complexity implies greater interspersion of open water and vegetation, which provides more opportunity for organic matter to be in contact with moving water and thus be exported. In calculations, is excluded automatically (cell goes blank) if wetland never has surface water during an average year or if no surface inflows."]
[null,null,{"$f":"F!C110","v":"Does not bump into plant stems as it travels through the AA.  Nearly all the water continues to travel in unvegetated (often incised) channels that have little contact with wetland vegetation, or through a zone of open water such as an instream pond or lake."},{"$f":"F!D110","v":0},1,{"$f":"D63*E63","v":0}]
[null,null,{"$f":"F!C111","v":"bumps into herbaceous vegetation but mostly remains in fairly straight channels."},{"$f":"F!D111","v":0},2,{"$f":"D64*E64","v":0}]
[null,null,{"$f":"F!C112","v":"bumps into herbaceous vegetation and mostly spreads throughout, or is in widely  meandering, multi-branched, or braided channels."},{"$f":"F!D112","v":0},4,{"$f":"D65*E65","v":0}]
[null,null,{"$f":"F!C113","v":"bumps into tree trunks and/or shrub stems but mostly remains in fairly straight channels."},{"$f":"F!D113","v":0},3,{"$f":"D66*E66","v":0}]
[null,null,{"$f":"F!C114","v":"bumps into tree trunks and/or shrub stems and follows a fairly indirect path from entrance to exit (meandering, multi-branched, or braided)"},{"$f":"F!D114","v":0},4,{"$f":"D67*E67","v":0}]
[{"$f":"F!A115","v":"F26"},{"$f":"F!B115","v":"Channel Connection & Outflow Duration"},{"$f":"F!C115","v":"The most persistent surface water connection (outlet channel or pipe, ditch, or overbank water exchange) between the AA and the closest off-site downslope water body is:"},null,null,null,{"$f":"IF((AllSat+AllSat1>0),\"\",MAX(F69:F73)/MAX(E69:E73))","v":0},"OutDura6","Streams are an important transporter of protein-rich, labile DOM in temperate watersheds (Fellman et al. 2009). Thus, annual export of accumulated organic matter to downstream water can be greater in wetlands with outlets, especially those with persistent outflow.  Nonetheless, even wetlands that lack outlets may export variable amounts of dissolved carbon via subsurface infiltration and \"pipes\" created by decayed subsurface peat and tree roots which cannot be evaluated in a rapid assessment. In calculations, is excluded automatically (cell goes blank) if wetland never has surface water during an average year."]
[null,null,{"$f":"F!C116","v":"persistent (>9 months/year, including times when frozen)"},{"$f":"F!D116","v":0},5,{"$f":"D69*E69","v":0}]
[null,null,{"$f":"F!C117","v":"seasonal (14 days to 9 months/year, not necessarily consecutive, including times when frozen)"},{"$f":"F!D117","v":0},4,{"$f":"D70*E70","v":0}]
[null,null,{"$f":"F!C118","v":"temporary (<14 days, not necessarily consecutive -- must be unfrozen)"},{"$f":"F!D118","v":0},3,{"$f":"D71*E71","v":0}]
[null,null,{"$f":"F!C119","v":"none -- but maps show a stream or other water body that is downslope from the AA and within a distance that is less than the AA's length.  If so, mark \"1\" here and SKIP TO F28 (Groundwater). "},{"$f":"F!D119","v":0},1,{"$f":"D72*E72","v":0}]
[null,null,{"$f":"F!C120","v":"no surface water flows out of the wetland except possibly during extreme events (<once per 10 years). Or, water flows only into a wetland, ditch, or lake that lacks an outlet.  If so, mark \"1\" here and SKIP TO F28 (Groundwater). "},{"$f":"F!D120","v":0},0,{"$f":"D73*E73","v":0}]
[{"$f":"F!A121","v":"F27"},{"$f":"F!B121","v":"Outflow Confinement"},{"$f":"F!C121","v":"During major runoff events, in the places where surface water exits the AA or connected waters nearby, it:"},null,null,null,{"$f":"IF((OutNone + OutNone1>0),\"\",MAX(F75:F77)/MAX(E75:E77))","v":0},"Constric6","Narrow outlets limit water outflow from a wetland and its downstream or downslope movement, thus limiting export of organic matter. The types of outlets described here are ones that typically are more constricted than natural channels, which usually have adjusted over time to local runoff and thus are wider relative to volume of flow received. In calculations, is excluded automatically (cell goes blank) if no outlet."]
[null,null,{"$f":"F!C122","v":"mostly passes through a pipe, culvert, narrowly breached dike, berm, beaver dam, or other partial obstruction (other than natural topography) that does not appear to drain the wetland artificially during most of the growing season."},{"$f":"F!D122","v":0},0,{"$f":"D75*E75","v":0}]
[null,null,{"$f":"F!C123","v":"leaves through natural exits (channels or diffuse outflow), not mainly through artificial or temporary features"},{"$f":"F!D123","v":0},1,{"$f":"D76*E76","v":0}]
[null,null,{"$f":"F!C124","v":"exported more quickly than usual due to ditches or pipes within the AA (or connected to its outlet or within 10 m of the AA's edge) which drain the wetland artificially, or water is pumped out of the AA."},{"$f":"F!D124","v":0},2,{"$f":"D77*E77","v":0}]
[{"$f":"F!A129","v":"F29"},{"$f":"F!B129","v":"Internal Gradient"},{"$f":"F!C129","v":"The gradient along most of the flow path within the AA is:"},null,null,null,{"$f":"MAX(F79:F82)/MAX(E79:E82)","v":0},"Gradient6","Steeper gradients imply a greater likelihood that whatever organic matter is produced will be transported offsite."]
[null,null,{"$f":"F!C130","v":"<2%, or, no slope is ever apparent (i.e., flat). Or, the wetland is in a depression or pond with no inlet and no outlet."},{"$f":"F!D130","v":0},0,{"$f":"D79*E79","v":0}]
[null,null,{"$f":"F!C131","v":"2-5%"},{"$f":"F!D131","v":0},2,{"$f":"D80*E80","v":0}]
[null,null,{"$f":"F!C132","v":"6-10%"},{"$f":"F!D132","v":0},3,{"$f":"D81*E81","v":0}]
[null,null,{"$f":"F!C133","v":">10%"},{"$f":"F!D133","v":0},4,{"$f":"D82*E82","v":0}]
[{"$f":"F!A172","v":"F37"},{"$f":"F!B172","v":"Broad-leaved Deciduous Trees and Shrubs"},{"$f":"F!C172","v":"The percentage of the AA's tree or shrub cover that is broad-leaved deciduous and is taller than 1 meter is:"},null,null,null,{"$f":"IF((NoWoodyVeg=1),\"\",MAX(F84:F88)/MAX(E84:E88))","v":0},"Decid6","Leaf litter from deciduous shrubs and trees tends to break down and cycle in receiving waters more rapidly than that of coniferous trees and shrubs. In calculations, is excluded automatically (cell goes blank) if no woody vegetation in the wetland."]
[null,null,{"$f":"F!C173","v":"<1%, or largest patch occupies less than 0.01 hectare"},{"$f":"F!D173","v":0},0,{"$f":"D84*E84","v":0}]
[null,null,{"$f":"F!C174","v":"1-25% of the tree or shrub cover (whichever has more)"},{"$f":"F!D174","v":0},1,{"$f":"D85*E85","v":0}]
[null,null,{"$f":"F!C175","v":"25-50% of the tree or shrub cover (whichever has more)"},{"$f":"F!D175","v":0},2,{"$f":"D86*E86","v":0}]
[null,null,{"$f":"F!C176","v":"50-75% of the tree or shrub cover (whichever has more)"},{"$f":"F!D176","v":0},3,{"$f":"D87*E87","v":0}]
[null,null,{"$f":"F!C177","v":">75% of the tree or shrub cover (whichever has more)"},{"$f":"F!D177","v":0},4,{"$f":"D88*E88","v":0}]
[{"$f":"F!A178","v":"F38"},{"$f":"F!B178","v":"N Fixers"},{"$f":"F!C178","v":"The percent of the AA's shrub plus ground cover that is nitrogen-fixing plants (e.g., alder, baltic (wire) rush, sweetgale, lupine, clover, other legumes) is:"},null,null,null,{"$f":"MAX(F90:F94)/MAX(E90:E94)","v":0},"Nfixer6","Nitrogen added to a wetland by N-fixing plants can increase the wetland's overall plant productivity, potentially making more organic matter available for export. Presence of alder in conifer woodlands also can speed the decomposition of organic material from the conifers (Fyles & Fyles 1993) perhaps making it more useful for supporting aquatic life."]
[null,null,{"$f":"F!C179","v":"<1% or none"},{"$f":"F!D179","v":0},0,{"$f":"D90*E90","v":0}]
[null,null,{"$f":"F!C180","v":"1-25% of the shrub plus ground cover, in the AA or along its water edge (whichever has more)."},{"$f":"F!D180","v":0},1,{"$f":"D91*E91","v":0}]
[null,null,{"$f":"F!C181","v":"25-50% of the shrub plus ground cover, in the AA or along its water edge (whichever has more)."},{"$f":"F!D181","v":0},2,{"$f":"D92*E92","v":0}]
[null,null,{"$f":"F!C182","v":"50-75% of the shrub plus ground cover, in the AA or along its water edge (whichever has more)."},{"$f":"F!D182","v":0},3,{"$f":"D93*E93","v":0}]
[null,null,{"$f":"F!C183","v":">75% of the shrub plus ground cover, in the AA or along its water edge (whichever has more)."},{"$f":"F!D183","v":0},4,{"$f":"D94*E94","v":0}]
[{"$f":"F!A188","v":"F40"},{"$f":"F!B188","v":"Moss Extent"},{"$f":"F!C188","v":"Within the part of the AA that lacks persistent surface water, the cover of moss is:"},null,null,null,{"$f":"MAX(F96:F100)/MAX(E96:E100)","v":0},"Moss6","Although moss-covered wetlands tend to have lower annual productivity, the accumulated moss is very rich in carbon and other nutrients and if subject to flows that can export it, can make these wetlands significant contributors of these nutrients at a watershed scale."]
[null,null,{"$f":"F!C189","v":"<5% of the ground cover"},{"$f":"F!D189","v":0},0,{"$f":"D96*E96","v":0}]
[null,null,{"$f":"F!C190","v":"5-25% of the ground cover"},{"$f":"F!D190","v":0},1,{"$f":"D97*E97","v":0}]
[null,null,{"$f":"F!C191","v":"25-50% of the ground cover"},{"$f":"F!D191","v":0},2,{"$f":"D98*E98","v":0}]
[null,null,{"$f":"F!C192","v":"50-95% of the ground cover"},{"$f":"F!D192","v":0},3,{"$f":"D99*E99","v":0}]
[null,null,{"$f":"F!C193","v":">95% of the ground cover"},{"$f":"F!D193","v":0},4,{"$f":"D100*E100","v":0}]
[{"$f":"F!A194","v":"F41"},{"$f":"F!B194","v":"% Bare Ground & Thatch"},{"$f":"F!C194","v":"Consider the parts of the AA that lack surface water at the driest time of the growing season.  Viewed from directly above the ground layer, the predominant condition in those areas at that time is:"},null,null,null,{"$f":"MAX(F102:F105)/MAX(E102:E105)","v":0},"Gcover6","More extensive ground cover may imply more organic matter is available for export.  Excessive litter buildup sometimes implies a lack of significant exporting forces, e.g., currents."]
[null,null,{"$f":"F!C195","v":"Little or no (<5%) bare ground is visible between erect stems or under canopy anywhere in the vegetated AA. Ground is extensively blanketed by dense thatch, moss, lichens, graminoids with great stem densities, or plants with ground-hugging foliage. "},{"$f":"F!D195","v":0},3,{"$f":"D102*E102","v":0}]
[null,null,{"$f":"F!C196","v":"Slightly bare ground (5-20% bare between plants) is visible in places, but those areas comprise less than 5% of the unflooded parts of the AA."},{"$f":"F!D196","v":0},2,{"$f":"D103*E103","v":0}]
[null,null,{"$f":"F!C197","v":"Much bare ground (20-50% bare between plants) is visible in places, and those areas comprise more than 5% of the unflooded parts of the AA. "},{"$f":"F!D197","v":0},1,{"$f":"D104*E104","v":0}]
[null,null,{"$f":"F!C198","v":"Other conditions"},{"$f":"F!D198","v":0},0,{"$f":"D105*E105","v":0}]
[{"$f":"F!A208","v":"F44"},{"$f":"F!B208","v":"Soil Texture"},{"$f":"F!C208","v":"In parts of the AA that lack persistent water, the texture of soil in the uppermost layer is mostly:  [To determine this, use a trowel to check in at least 3 widely spaced locations, and use the soil texture key in Appendix A of the Manual]"},null,null,null,{"$f":"MAX(F107:F110)/MAX(E107:E110)","v":0},"SoilTex6","Soils with a thick organic layer have the most carbon available for export. However, moderately coarse soils (silts, loams) are better-aerated, less acidic, and thus can have greater plant productivity. Very coarse soils, unless flooded regularly by rivers, tend to be nutrient-poor thus limiting plant productivity. However, their presence may indicate periodic exposure to water currents capable of exporting carbon, and coarse soils sometimes support greater plant productivity because greater inflitration can reduce the frequency of anoxic conditions that stifle productivity of some rooted plants. "]
[null,null,{"$f":"F!C209","v":"Loamy: includes loam, sandy loam"},{"$f":"F!D209","v":0},1,{"$f":"D107*E107","v":0}]
[null,null,{"$f":"F!C210","v":"Fines: includes silt, glacial flour, clay, clay loam, silty clay, silty clay loam, sandy clay, sandy clay loam."},{"$f":"F!D210","v":0},2,{"$f":"D108*E108","v":0}]
[null,null,{"$f":"F!C211","v":"Organic"},{"$f":"F!D211","v":0},4,{"$f":"D109*E109","v":0}]
[null,null,{"$f":"F!C212","v":"Coarse: includes sand, loamy sand, gravel, cobble, stones, boulders, fluvents, fluvaquents, riverwash."},{"$f":"F!D212","v":0},0,{"$f":"D110*E110","v":0}]
[{"$f":"F!A259","v":"F55"},{"$f":"F!B259","v":"New Wetland"},{"$f":"F!C259","v":"The AA is (or is within, or contains) a \"new\" wetland resulting from human actions (e.g., excavation, impoundment) or debris flows,  or other factors affecting what once was upland (non-hydric) soil."},null,null,null,{"$f":"IF((D117=1),\"\",MAX(F112:F116)/MAX(E112:E116))","v":0},"NewWet6","Soil organic matter is slow to accumulate in constructed wetlands (Alsfeld et al. 2009), so less is likely to be available for export. "]
[null,null,{"$f":"F!C260","v":"No"},{"$f":"F!D260","v":0},5,{"$f":"D112*E112","v":0}]
[null,null,{"$f":"F!C261","v":"yes, and created 20 - 100 years ago "},{"$f":"F!D261","v":0},2,{"$f":"D113*E113","v":0}]
[null,null,{"$f":"F!C262","v":"yes, and created 3-20 years ago"},{"$f":"F!D262","v":0},1,{"$f":"D114*E114","v":0}]
[null,null,{"$f":"F!C263","v":"yes, and created within last 3 years"},{"$f":"F!D263","v":0},0,{"$f":"D115*E115","v":0}]
[null,null,{"$f":"F!C264","v":"yes, but time of origin unknown"},{"$f":"F!D264","v":0},1,{"$f":"D116*E116","v":0}]
[null,null,{"$f":"F!C265","v":"unknown if new within 20 years or not"},{"$f":"F!D265","v":0}]
[null,null,null,null,null,null,null," "]
[null,null,"Organic Matter Stock [Cstock]"]
[null,"Wetlands <10 hectares:","AVERAGE(FenBogMarsh, WetVegArea, OWpct6, SoilTex6, SoilOrgPct, Moss6, Stained6, Fluctu6, NewWet6, VwidthAbs6)",null,null,null,{"$f":"IF((GT10HA=1),G121, IFERROR(AVERAGE(FenBogMarsh, WetVegArea, OWpct6,SoilTex6, SoilOrgPct,Moss6, Stained6, Fluctu6, NewWet6, VwidthAbs6),\"\"))","v":0}]
[null,"Wetlands >10 hectares:","Substituted 1-OWPct, SoilTex",null,null,null,{"$f":"IFERROR(AVERAGE(FenBogMarsh, WetVegArea, 1-OWpct,SoilTex_NROE, SoilOrgPct,Moss6, Stained6, Fluctu6, NewWet6, VwidthAbs6),\"\")","v":0.25}]
[]
[null,null,"Decomposition and Mobility [LabileC]"]
[null,"Wetlands <10 hectares:","AVERAGE(GrowDD, Wettype6, Gradient6, Interspers6, ThruFlo6, Gcover6, PondedPct6, SeasWpct6, Shade6, Decid6, Nfixer6)",null,null,null,{"$f":"IF((GT10HA=1),G125, IFERROR(AVERAGE(GrowDD, Wettype6, Gradient6, Interspers6, ThruFlo6, Gcover6, PondedPct6, SeasWpct6, Shade6, Decid6, Nfixer6),\"\"))","v":0}]
[null,"Wetlands >10 hectares:","Added LGIndex, substituted MixWaterVeg, ",null,null,null,{"$f":"IFERROR(AVERAGE(GrowDD, Wettype6, LGIndex, Gradient6, MixWaterVeg, Interspers6, ThruFlo6, Gcover6, PondedPct6, SeasWpct6, Shade6, Decid6, Nfixer6),\"\")","v":0}]
[]
[null,null,"Export [OutC]"]
[null,null,"AVERAGE(Constric6, OutDura6, RipFloodpl)",null,null,null,{"$f":"IFERROR(AVERAGE(Constric6, OutDura6, RipFloodpl),\"\")","v":0}]
[]
[null,null,"ABWRET-A FUNCTION MODEL"]
[null,null,"Organic Nutrient Export"]
[null,null,"IF((OutNone + OutNone1>0), 0, ELSE: AVERAGE(CStock, LabileC, OutC)",null,null,null,{"$f":"IF((OutNone + OutNone1>0),0, 10*AVERAGE(Cstock1a, LabileC1a, OutC1a))","v":0}]
[null,null,null,null,null,null,null,null,"Literature Cited"]
[null,null,"ABWRET-E model",null,null,null,null,null,"Alsfeld, A. J., J. L. Bowman, and A. Deller-Jacobs. 2009. Effects of woody debris, microtopography, and organic matter amendments on the biotic community of constructed depressional wetlands. Biological Conservation 142:247-255."]
[null,1,"IF(ChannConn + RipFloodPl = 0), then = 0",{"$f":"IF((ChannConn+RipFloodpl=0), 0, \"\")","v":0},null,null,null,null,"Bayley, S. E. and R. L. Mewhort. 2004. Plant community structure and junctional differences between marshes and fens in the southern boreal region of Alberta, Canada. Wetlands 24:277-294."]
[null,2,"ELSE calculate these averages:",null,null,null,null,null,"D'Amore, D. V., J. B. Fellman, R. T. Edwards, and E. Hood. 2010. Controls on dissolved organic matter concentrations in soils and streams from a forested wetland and sloping bog in southeast Alaska. Ecohydrology 3:249-261."]
[null,"a","AVERAGE(SoilTex, SoilOrgPct, FenBogMarsh)",{"$f":"IFERROR(AVERAGE(SoilTex_NROE, SoilOrgPct, FenBogMarsh),\"\")","v":""},null,null,null,null,"Devito, K. J., P. J. Dillon, and B. D. Lazerte. 1989. Phosphorus and nitrogen retention in five Precambrian shield wetlands. Biogeochemistry 8:185–204."]
[null,"b","AVERAGE(GrowDD, WetVegArea)",{"$f":"IFERROR(AVERAGE(GrowDD, WetVegArea),\"\")","v":""},null,null,null,null,"Fellman, J. B., E. Hood, D. V. D'Amore, R. T. Edwards, and D. White. 2009. Seasonal changes in the chemical quality and biodegradability of dissolved organic matter exported from soils to streams in coastal temperate rainforest watersheds. Biogeochemistry 95:277-293."]
[null,3,"10* AVERAGE(MixWaterVeg, a, b)",{"$f":"IF((D135=0),0, 10* AVERAGE(MixWaterVeg, D137, D138))","v":0},null,null,null,null,"Fissore, C., Giardina, C. P., Kolka, R. K., and Trettin, C. C. 2009. Soil organic carbon quality in forested mineral wetlands at different mean annual temperature. Soil Biology and Biochemistry 41(3):458-466."]
[null,null,null,null,null,null,null,null,"Fitzgerald, D. F., J. S. Price, and J. J. Gibson. 2003. Hillslope-swamp interactions and flow pathways in a hyper-maritime rainforest, British Columbia. Hydrological Processes 17:3005-3022."]
[null,null,"ABWRET-E with substitutions:",null,null,null,null,null,"Fyles, J. W. and I. H. Fyles. 1993. Interaction of Douglas-fir with red alder and salal foliage litter during decomposition. Canadian Journal of Forest Research 23:358-361."]
[null,1,"IF(OutNone+OutNone1>0), then =0",{"$f":"IF((OutNone+OutNone1>0), 0, \"\")","v":""},null,null,null,null,"Glenn, A. J., L. B. Flanagan, K. H. Syed, and P. J. Carlson. 2006. Comparison of net ecosystem CO2 exchange in two peatlands in western Canada with contrasting dominant vegetation, Sphagnum and Carex. Agricultural and Forest Meteorology 140:115-135."]
[null,2,"ELSE calculate these averages:",null,null,null,null,null,"Gunnarsson, U. 2005. Global patterns of Sphagnum productivity. Journal of Bryology 27:269-279."]
[null,"a","AVERAGE(SoilTex6, SoilOrgPct, FenBogMarsh)",{"$f":"IFERROR(AVERAGE(SoilTex6, SoilOrgPct, FenBogMarsh),\"\")","v":0},null,null,null,null,"MacKenzie, W. and J. Shaw. 2000. Wetland classification and habitats at risk in British Columbia.  Volume Two. Pages 537-547 in L. M. Darling, editor. Proceedings of a Conference on the Biology and Management of Species and Habitats at Risk, Kamloops, B.C.,15 - 19 Feb.,1999. B.C. Ministry of Environment, Lands and Parks, Victoria, B.C. and University College of the Cariboo, Kamloops, B.C. ."]
[null,"b","AVERAGE(GrowDD, WetVegArea)",{"$f":"IFERROR(AVERAGE(GrowDD, WetVegArea),\"\")","v":""},null,null,null,null,"Pacific, V. J., K. G. Jensco, and B. L. McGlynn. 2010. Variable flushing mechanisms and landscape structure control stream DOC export during snowmelt in a set of nested catchments. Biogeochemistry 99:193-211."]
[null,3,"10* AVERAGE(Interspers6, a, b)",{"$f":"IF((D142=0),0, 10* AVERAGE(Interspers6, D144, D145))","v":0}]

{"sheet":"FH","index":16,"n_rows":159,"n_cols":10,"rows_kept":159,"cut":false,"hidden":false,"merged":[[133,0,134,0],[84,0,89,0],[90,0,95,0],[96,0,99,0],[106,0,110,0],[100,0,105,0],[90,1,95,1],[129,0,130,0],[84,1,89,1],[96,1,99,1],[100,1,105,1],[106,1,110,1],[106,8,110,8],[100,8,105,8],[73,8,76,8],[73,7,76,7],[106,7,110,7],[100,7,105,7],[79,7,83,7],[84,7,89,7],[90,7,95,7],[96,7,99,7],[96,8,99,8],[90,8,95,8],[79,8,83,8],[84,8,89,8],[54,8,61,8],[50,7,53,7],[69,7,72,7],[54,7,61,7],[62,7,68,7],[69,8,72,8],[62,8,68,8],[79,0,83,0],[62,1,68,1],[73,0,76,0],[73,1,76,1],[54,1,61,1],[54,0,61,0],[69,0,72,0],[69,1,72,1],[79,1,83,1],[0,0,0,1],[44,0,49,0],[62,0,68,0],[29,1,35,1],[36,1,41,1],[22,0,28,0],[22,1,28,1],[36,0,41,0],[44,1,49,1],[17,1,21,1],[29,0,35,0],[50,1,53,1],[50,0,53,0],[117,7,118,7],[117,8,118,8],[111,8,116,8],[111,1,116,1],[111,0,116,0],[111,7,116,7],[117,0,118,0],[117,1,118,1],[0,4,0,8],[17,8,21,8],[50,8,53,8],[44,8,49,8],[36,8,41,8],[29,8,35,8],[22,8,28,8],[29,7,35,7],[17,7,21,7],[22,7,28,7],[36,7,41,7],[44,7,49,7]]}
["Fish                   Habitat",null,"The capacity to support an abundance and diversity of native fish species.  ","FH"]
["#","Function Indicators from Estimator","Scoring Notes",null,null,null,"Normalised Score","Indicator Abbreviation or Formula","Rationale"]
[{"$f":"OF!A5","v":"OF4"},{"$f":"OF!C5","v":"Channel Connection"},"If no connection, then blank (NULL) and ignored in calculations rather than reducing the indicator score.",null,null,null,{"$f":"IF((ChannConn=\"\"),\"\",ChannConn)","v":""},"ChannConn","Although fish are common in isolated wetlands (at least, those that have permanent water), wetlands with a surface water connection to other water bodies usually support greater fish production and diversity and are less prone to winterkill problems."]
[{"$f":"OF!A9","v":"OF8"},{"$f":"OF!C9","v":"Distance to Nearest Road (from Wetland Edge)"},null,null,null,null,{"$f":"IF((Dist2Road=\"\"),\"\",Dist2Road)","v":""},"Dist2Road","Road access potentially brings more fishing pressure and pollutants, so increasing distance from roads is assumed to be better for fish populations."]
[{"$f":"OF!A16","v":"OF15"},{"$f":"OF!C16","v":"Fish Presence"},"If wetland not intersected by a Class A or B stream (Alberta Water Act Codes of Practice stream), then cell turns blank (NULL) and is ignored in calculations rather than reducing the indicator score.  The data source is not comprehensive and does not include lakes and ponds.",null,null,null,{"$f":"IF((FishPres=\"\"),\"\",IF((FishPres=1),1,\"\"))","v":""},"FishPres","This is direct evidence of fish use, though not necessarily fish diversity."]
[{"$f":"OF!A18","v":"OF17"},{"$f":"OF!C18","v":"Growing Degree Days"},null,null,null,null,{"$f":"IF((GrowDD=\"\"),\"\",GrowDD)","v":""},"GrowDD","Plants are more productive at warmer soil or sediment temperatures, and this supports higher productivity of aquatic insects and ultimately resident fish. "]
[{"$f":"OF!A28","v":"OF27"},{"$f":"OF!C28","v":"Interspersion Index for Internal Water & Vegetation (macroscale)"},null,null,null,null,{"$f":"IF((MixWaterVeg=\"\"),\"\",MixWaterVeg)","v":""},"MixWaterVeg","More interspersion of vegetation with open water is likely to support more fish biomass and diversity because it implies more access of fish to vegetated areas that contain rich food sources (invertebrates inhabiting plants and the sediment surface)."]
[{"$f":"OF!A31","v":"OF30"},{"$f":"OF!C31","v":"% of AA that is Open Water (macro scale)"},null,null,null,null,{"$f":"IF((OWpct=\"\"),\"\",OWpct)","v":""},"OWpct","Open water does not restrict fish movements, whereas in vegetated wetlands (especially Bog, Fen, Swamp) fish movements are partly or completely restricted by lack of water or water that is often too shallow."]
[{"$f":"OF!A35","v":"OF34"},{"$f":"OF!C35","v":"% of Wetland Perimeter Adjoined by Natural Cover"},null,null,null,null,{"$f":"IF((PerimNatCov=\"\"),\"\",PerimNatCov)","v":""},"PerimNatCov","Increased natural cover along the perimeter helps filter pollutants and provides insect foods and sometimes shade.  Degraded water quality (particularly lowered dissolved oxygen resulting from die-offs of algal blooms) can limit fish populations, especially in wetlands, ponds, and lakes. However, some studies of prairie wetlands (Hanson 2012 ) have found that fish populations are influenced more by in-pond factors than by surrounding land use."]
[{"$f":"OF!A41","v":"OF40"},{"$f":"OF!C41","v":"Road Density in 1km Buffer"},null,null,null,null,{"$f":"IF((RdDens1k=\"\"),\"\",RdDens1k)","v":""},"RdDens1k","Road density is an index of fishing pressure as well as potential impacts from stormwater runoff, reduced fish access, and channel form changes."]
[{"$f":"OF!A43","v":"OF42"},{"$f":"OF!C43","v":"Riparian or Floodway Location"},"If wetland not intersected by a mapped riparian area or floodplain, then cell turns blank (NULL) and is ignored in calculations rather than reducing the indicator score. ",null,null,null,{"$f":"IF((RipFloodpl=\"\"),\"\",IF((RipFloodpl=1),1,\"\"))","v":""},"RipFloodpl","Floodplain and riparian areas that flood only occasionally are  important to fish during the brief times of flooding, as shelter from strong currents and because they provide terrestrial invertebrate foods that fall from vegetation or are flushed out of newly flooded soils."]
[{"$f":"OF!A51","v":"OF50"},{"$f":"OF!C51","v":"Springs within 300m"},null,null,null,null,{"$f":"IF((Spring=\"\"),\"\",Spring)","v":""},"Spring","Springs provide a relatively stable thermal environment and a steady input of nutrients that supports algal production and the invertebrate foods important to resident fish."]
[{"$f":"OF!A52","v":"OF51"},{"$f":"OF!C52","v":"Subzero Days"},"Inverse",null,null,null,{"$f":"IF((Sub0Days=\"\"),\"\",1-Sub0Days)","v":""},"Sub0Days","Risk of winterkill by long-duration ice cover also may be less in warmer parts of the region."]
[{"$f":"OF!A61","v":"OF60"},{"$f":"OF!C61","v":"Water Permanence Probability"},null,null,null,null,{"$f":"IF((WatProb=\"\"),\"\",WatProb)","v":""},"WatProb","Wetlands that lack permanent surface water do not support fish unless a channel or floodplain is present (that presumably connects to more permanent waters)."]
[{"$f":"OF!A63","v":"OF62"},{"$f":"OF!C63","v":"AA Size"},null,null,null,null,{"$f":"IF((WetArea=\"\"),\"\",WetArea)","v":""},"WetArea","The extent of surface water in a lake or fish-accessible wetland is one of the strongest predictors of overwinter fish survival in Alberta (Paszkowski & Tonn 2001). "]
[{"$f":"OF!A73","v":"OF72"},{"$f":"OF!C73","v":"Surface Water Quality Risk Index"},"Inverse",null,null,null,{"$f":"IF((WQrisk=\"\"),\"\",1-WQrisk)","v":""},"WQrisk","Pesticides and some other chemicals associated with agricultural and developed areas can harm fish, if not directly then by decimating the invertebrate foods upon which fish depend.  However, this index from the Agricultural Land Resource Atlas of Alberta was mapped at a coarse scale with outdated information on pesticide and fertiliser use."]
["#","Function Indicators from Onsite Visit","Categorical Choices","Data","Weight","Data  x  Weight","Normalised Score","Indicator Abbreviation or Formula","Rationale & Scoring Notes"]
[{"$f":"F!A6","v":"F1"},{"$f":"F!B6","v":"Wetland Type - Predominant"},{"$f":"F!C6","v":"Most of the vegetated part of the AA (wetland Assessment Area) is a (select ONE):"},null,null,null,{"$f":"MAX(F19:F22)/MAX(E19:E22)","v":0},"Wettype10","Of the wetland types listed, marsh and fen wetlands are typically most important because they have the most water and are the most accessible to resident fish. Wooded swamps can be important as well if they are in floodplains and at least intermittently accessible to fish. "]
[{"$f":"F!A7","v":"F1.1"},null,{"$f":"F!C7","v":"Wooded Swamp"},{"$f":"F!D7","v":0},1,{"$f":"D19*E19","v":0}]
[{"$f":"F!A8","v":"F1.2"},null,{"$f":"F!C8","v":"Bog"},{"$f":"F!D8","v":0},0,{"$f":"D20*E20","v":0}]
[{"$f":"F!A9","v":"F1.3"},null,{"$f":"F!C9","v":"Fen"},{"$f":"F!D9","v":0},3,{"$f":"D21*E21","v":0}]
[{"$f":"F!A10","v":"F1.4"},null,{"$f":"F!C10","v":"Marsh or Shallow Open Water"},{"$f":"F!D10","v":0},4,{"$f":"D22*E22","v":0}]
[{"$f":"F!A17","v":"F3"},{"$f":"F!B17","v":"% Saturated Only"},{"$f":"F!C17","v":"The percentage of the AA that never contains surface water during an average year (that is, except perhaps for a few hours after snowmelt or rainstorms), but which is still a wetland, is:"},null,null,null,{"$f":"MAX(F24:F29)/MAX(E24:E29)","v":0},"SatPct10","Used as a classifier. Wetlands that are never inundated cannot support resident fish."]
[null,null,{"$f":"F!C18","v":"less than 1%, or <0.01 hectare (about 10 m on a side) never has surface water.  In other words, all or nearly all of the AA is inundated permanently or at least seasonally."},{"$f":"F!D18","v":0},5,{"$f":"D24*E24","v":0}]
[null,null,{"$f":"F!C19","v":"1-25% of the AA never contains surface water."},{"$f":"F!D19","v":0},4,0]
[null,null,{"$f":"F!C20","v":"25-50% of the AA never contains surface water."},{"$f":"F!D20","v":0},3,0]
[null,null,{"$f":"F!C21","v":"50-99% of the AA never contains surface water."},{"$f":"F!D21","v":0},2,0]
[null,null,{"$f":"F!C22","v":">99% of the AA never contains surface water, except for water flowing in channels and/or in pools that occupy <1% of the AA. SKIP to F26 (Channel Connection & Outflow Duration)"},{"$f":"F!D22","v":0},1,0]
[null,null,{"$f":"F!C23","v":">99% of the AA never contains surface water, and AA is not intersected by channels that have flow, not even for a few days per year. SKIP to F26."},{"$f":"F!D23","v":0},0,0]
[{"$f":"F!A24","v":"F4"},{"$f":"F!B24","v":"% with Persistent Surface Water"},{"$f":"F!C24","v":"The percentage of the AA that has surface water (either ponded or flowing, either open or obscured by vegetation) during all of the growing season during most years is:"},null,null,null,{"$f":"IF((AllSat+AllSat1>0),\"\",MAX(F31:F36)/MAX(E31:E36))","v":0},"PermWpct10","Persistent surface water is essential to resident fish in isolated wetlands, and is important to resident fish even in wetlands that connect seasonally to other water bodies. In calculations, is excluded automatically (cell goes blank) if wetland never has surface water during an average year. "]
[null,null,{"$f":"F!C25","v":"less than 1%, or <0.01 hectare (whichever is less).  SKIP to F8 (% Flooded Only Seasonally)."},{"$f":"F!D25","v":0},0,{"$f":"D31*E31","v":0}]
[null,null,{"$f":"F!C26","v":"1-25% of the AA, and mostly in narrow channels and/or small scattered pools."},{"$f":"F!D26","v":0},1,{"$f":"D32*E32","v":0}]
[null,null,{"$f":"F!C27","v":"1-25% of the AA, and mostly in a single large pool, pond, and/or channel."},{"$f":"F!D27","v":0},2,{"$f":"D33*E33","v":0}]
[null,null,{"$f":"F!C28","v":"25-50% of the AA"},{"$f":"F!D28","v":0},3,{"$f":"D34*E34","v":0}]
[null,null,{"$f":"F!C29","v":"50-95% of the AA"},{"$f":"F!D29","v":0},4,{"$f":"D35*E35","v":0}]
[null,null,{"$f":"F!C30","v":">95% of the AA"},{"$f":"F!D30","v":0},5,{"$f":"NoPermW10*E36","v":0}]
[{"$f":"F!A31","v":"F5"},{"$f":"F!B31","v":"% of Summertime Water That Is Shaded"},{"$f":"F!C31","v":"At mid-day during the warmest time of year, the area of surface water within the AA that is shaded (by emergent or woody vegetation, incised channels, streambanks, or other features also present within the AA) is:"},null,null,null,{"$f":"IF((AllSat+AllSat1>0),\"\", IF((NoPersis=1),\"\", MAX(F38:F42)/MAX(E38:E42)))","v":0},"Shade10","Shade helps maintain stable water temperatures favorable to resident fish. Vegetation associated with shading increases the availability of terrestrial insects that fall off the shading vegetation and into waters where they are fed upon by fish. However, shade also can reduce algal biomass and thus the abundance of aquatic insects fed upon by some resident fish. In calculations, is excluded automatically (cell goes blank) if wetland never has surface water during an average year or if water is present only seasonally."]
[null,null,{"$f":"F!C32","v":"<5% of the water is shaded, or no surface water is present then."},{"$f":"F!D32","v":0},0,{"$f":"D38*E38","v":0}]
[null,null,{"$f":"F!C33","v":"5-25% of the water is shaded"},{"$f":"F!D33","v":0},1,{"$f":"D39*E39","v":0}]
[null,null,{"$f":"F!C34","v":"25-50% of the water is shaded"},{"$f":"F!D34","v":0},2,{"$f":"D40*E40","v":0}]
[null,null,{"$f":"F!C35","v":"50-75% of the water is shaded"},{"$f":"F!D35","v":0},4,{"$f":"D41*E41","v":0}]
[null,null,{"$f":"F!C36","v":">75% of the water is shaded"},{"$f":"F!D36","v":0},3,{"$f":"D42*E42","v":0}]
[{"$f":"F!A37","v":"F6"},{"$f":"F!B37","v":"Fringe Wetland"},{"$f":"F!C37","v":"If the AA meets the following conditions, it is a fringe wetland: (a) Open water that adjoins the vegetated wetland in a lake, stream, or river during annual low water condition is much wider than the vegetated wetland, and if the AA adjoins a lake (b) the maximum dimension of the lake is greater than 1 km. If true, enter \"1\" and continue."},{"$f":"F!D37","v":0},null,null,{"$f":"IF((AllSat+AllSat1>0),\"\", IF((NoPersis=1),\"\", IF((D43=0),\"\",1)))","v":""},"Fringe10","Because their connectivity with adjoining water bodies is more certain, fringe wetlands often provide better conditions for fish, allowing escape from occasional drought and low oxygen conditions.  In calculations, is excluded automatically (cell goes blank) if wetland never has surface water during an average year or if water is present only seasonally.  If condition not met, then ignored in calculations rather than being counted as a negative."]
[{"$f":"F!A38","v":"F7"},{"$f":"F!B38","v":"Lacustrine Wetland"},{"$f":"F!C38","v":"The AA borders a body of ponded open water whose size -- not counting the vegetated AA -- exceeds 8 hectares (about 300 x 300 m) during most of the growing season.  Enter \"1\" if true, \"0\" if false."},{"$f":"F!D38","v":0},null,null,{"$f":"IF((AllSat+AllSat1>0),\"\", IF((NoPersis=1),\"\", IF((D44=0),\"\",1)))","v":""},"Lake10","Even if not connected to other water bodies, lakes are used extensively by resident fish, and lakeside wetlands provide shelter, rich feeding areas, and substrate for spawning by some species. In calculations, is excluded automatically (cell goes blank) if wetland never has surface water during an average year or if water is present only seasonally.  If condition not met, then ignored in calculations rather than being counted as a negative."]
[{"$f":"F!A52","v":"F10"},{"$f":"F!B52","v":"Predominant Depth Class"},{"$f":"F!C52","v":"During most of the time when water is present, its depth in most of the area is: [Note: This is not asking for the maximum depth.]"},null,null,null,{"$f":" IF((AllSat+AllSat1>0),\"\", IF((SmallAA=1),\"\", MAX(F46:F50)/MAX(E46:E50)))","v":0},"Depth10","Most resident fish spend much of their time in deeper water because of the cover it provides. Wetlands with deeper water provide more habitat space. In calculations, is excluded automatically (cell goes blank) if wetland never has surface water during an average year. Also is excluded automatically if wetland is <0.01 ha."]
[null,null,{"$f":"F!C53","v":"<10 cm deep (but >0)"},{"$f":"F!D53","v":0},0,{"$f":"D46*E46","v":0}]
[null,null,{"$f":"F!C54","v":"10 - 50 cm deep"},{"$f":"F!D54","v":0},1,0]
[null,null,{"$f":"F!C55","v":"0.5 - 1 m deep"},{"$f":"F!D55","v":0},2,0]
[null,null,{"$f":"F!C56","v":"1 - 2 m deep"},{"$f":"F!D56","v":0},3,0]
[null,null,{"$f":"F!C57","v":">2 m deep.  True for many fringe wetlands."},{"$f":"F!D57","v":0},4,0]
[{"$f":"F!A58","v":"F11"},{"$f":"F!B58","v":"Depth Classes - Evenness of Proportions"},{"$f":"F!C58","v":"When present, surface water in most of the AA usually consists of (select one):"},null,null,null,{"$f":"IF((AllSat+AllSat1>0),\"\", IF((SmallAA=1),\"\", MAX(F52:F54)/MAX(E52:E54)))","v":0},"DepthEven10","Different resident fish species have different habitat needs, and a variety of depths within a wetland implies greater capacity of the wetland to meet the needs of multiple species.  /   In calculations, is excluded automatically (cell goes blank) if wetland never has surface water during an average year. Also is excluded automatically if wetland is <0.01 ha."]
[null,null,{"$f":"F!C59","v":"One depth class that comprises >90% of the AA’s inundated area (use the classes in the question above)."},{"$f":"F!D59","v":0},0,0]
[null,null,{"$f":"F!C60","v":"One depth class that comprises 60-90% of the AA's inundated area."},{"$f":"F!D60","v":0},1,0]
[null,null,{"$f":"F!C61","v":"Neither of above.  Multiple depth classes; none occupy more than 50% of the AA."},{"$f":"F!D61","v":0},2,0]
[{"$f":"F!A62","v":"F12"},{"$f":"F!B62","v":"% of Water Ponded vs. Flowing "},{"$f":"F!C62","v":"The percentage of the AA's surface water that is ponded (stagnant, or flows so slowly that fine sediment is not held in suspension) during most of the time it is present, and which is either open or shaded by emergent vegetation is:"},null,null,null,{"$f":" IF((AllSat+AllSat1>0),\"\", IF((SmallAA=1),\"\", MAX(F56:F62)/MAX(E56:E62)))","v":0},"IsoDry10","A mix of accessible ponded and flowing water is important to many fish species. In calculations, is excluded automatically (cell goes blank) if wetland is <0.01 ha."]
[null,null,{"$f":"F!C63","v":"<1% or none, or occupies <0.01 hectare cumulatively.  Nearly all water is flowing.  Enter \"1\" and SKIP to F21 (Stained Surface Water)."},{"$f":"F!D63","v":0},1,{"$f":"D56*E56","v":0}]
[null,null,{"$f":"F!C64","v":"1-5% of the water, and mainly in small pools.  The rest is flowing."},{"$f":"F!D64","v":0},2,0]
[null,null,{"$f":"F!C65","v":"1-5% of the water, and mainly in a single large pool or pond.  The rest is flowing."},{"$f":"F!D65","v":0},3,0]
[null,null,{"$f":"F!C66","v":"5-30% of the water"},{"$f":"F!D66","v":0},4,0]
[null,null,{"$f":"F!C67","v":"30-70% of the water"},{"$f":"F!D67","v":0},5,0]
[null,null,{"$f":"F!C68","v":"70-95% of the water"},{"$f":"F!D68","v":0},6,0]
[null,null,{"$f":"F!C69","v":">95% of the water.  Little or no visibly flowing water within the AA."},{"$f":"F!D69","v":0},5,0]
[{"$f":"F!A71","v":"F14"},{"$f":"F!B71","v":"% of Ponded Water That Is Open "},{"$f":"F!C71","v":"In ducks-eye aerial view, the percentage of the ponded water that is open (lacking emergent vegetation during most of the growing season, and unhidden by a forest or shrub canopy) is:"},null,null,null,{"$f":"IF((AllSat+AllSat1>0),\"\", IF((NoPonded=1),\"\", IF((SmallAA=1),\"\", MAX(F64:F68)/MAX(E64:E68))))","v":0},"OWpct10","Aquatic plants provide cover for fish and in some cases the associated shading helps maintain cool water temperature. However, as they decay beneath winter ice, they can deprive fish of necessary oxygen (Meding & Jackson 2003).  In calculations, is excluded automatically (cell goes blank) if wetland has no ponded water or is <0.01 ha."]
[null,null,{"$f":"F!C72","v":"<1% or none, or largest pool occupies <0.01 hectares.  Enter \"1\" and SKIP to F20 (Floating Algae & Duckweed)."},{"$f":"F!D72","v":0},0,{"$f":"D64*E64","v":0}]
[null,null,{"$f":"F!C73","v":"1-5% of the ponded water.  Enter \"1\" and SKIP to F20."},{"$f":"F!D73","v":0},2,{"$f":"D65*E65","v":0}]
[null,null,{"$f":"F!C74","v":"5-30% of the ponded water."},{"$f":"F!D74","v":0},3,{"$f":"D66*E66","v":0}]
[null,null,{"$f":"F!C75","v":"30-70% of the ponded water."},{"$f":"F!D75","v":0},2,{"$f":"D67*E67","v":0}]
[null,null,{"$f":"F!C76","v":"70-99% of the ponded water."},{"$f":"F!D76","v":0},0,{"$f":"D68*E68","v":0}]
[null,null,{"$f":"F!C77","v":"100% of the ponded water. "},{"$f":"F!D77","v":0}]
[{"$f":"F!A91","v":"F17"},{"$f":"F!B91","v":"Non-vegetated Aquatic Cover"},{"$f":"F!C91","v":"Near waters that are deeper than 0.5 m, the cover for fish, aquatic invertebrates, and/or amphibians that is provided by horizontally incised banks and/or partly-submerged accumulations of wood thicker than 10 cm (NOT by living vegetation) is:"},null,null,null,{"$f":"IF((OpenW=0),\"\", IF((SmallAA=1),\"\", MAX(F71:F73)/MAX(E71:E73)))","v":""},"WoodAbove10","Large woody debris helps protect young fish from aerial predators and provides cooler water preferred by salmonids. In calculations, is excluded automatically (cell goes blank) if wetland never has surface water during an average year. Also is excluded automatically if wetland lacks open water or is <0.01 ha."]
[null,null,{"$f":"F!C92","v":"Little or none, or all water is shallower than 0.5 m most of the year."},{"$f":"F!D92","v":0},0,{"$f":"D71*E71","v":0}]
[null,null,{"$f":"F!C93","v":"Intermediate"},{"$f":"F!D93","v":0},1,{"$f":"D72*E72","v":0}]
[null,null,{"$f":"F!C94","v":"Extensive"},{"$f":"F!D94","v":0},2,{"$f":"D73*E73","v":0}]
[{"$f":"F!A95","v":"F18"},{"$f":"F!B95","v":"Interspersion of Robust Emergents & Open Water"},{"$f":"F!C95","v":"During most of the growing season, the spatial pattern of tall robust herbaceous vegetation (e.g., cattail, bulrush) that has surface water beneath it is mostly:"},null,null,null,{"$f":"IF((AllSat+AllSat1>0),\"\", IF((NoPonded=1),\"\",IF((NoOpenPonded+NoOpenPonded1>0),\"\",IF((AllOpenPond=1),\"\", IF((SmallAA=1),\"\", MAX(F75:F77)/MAX(E75:E77))))))","v":0},"Interspers10","Greater interspersion of open water with vegetation provides resident fish with greater access to food sources, such as insects falling off emergent plants. In calculations, is excluded automatically (cell goes blank) if no ponded water, if ponded water but no vegetation, if ponded but no open water, or if <0.01 ha."]
[null,null,{"$f":"F!C96","v":"Scattered in small clumps, islands, or patches throughout the surface water area."},{"$f":"F!D96","v":0},3,{"$f":"D75*E75","v":0}]
[null,null,{"$f":"F!C97","v":"Intermediate"},{"$f":"F!D97","v":0},2,{"$f":"D76*E76","v":0}]
[null,null,{"$f":"F!C98","v":"Clumped at one or a few sides of the surface water area, or mostly surrounds a central area of open water.  Or such vegetation is absent or covers <9 sq m and <1% of the AA."},{"$f":"F!D98","v":0},1,{"$f":"D77*E77","v":0}]
[{"$f":"F!A101","v":"F21"},{"$f":"F!B101","v":"Stained Surface Water"},{"$f":"F!C101","v":"Most surface water is tea-colored (from tannins, not iron bacteria or silt), and/or its pH is usually <5.5. Nearby vegetation is mostly moss and/or conifers. "},{"$f":"F!D101","v":0},null,null,{"$f":"IF((AllSat+AllSat1>0),\"\",IF((SmallAA=1),\"\", IF((D78)=1,0,\"\")))","v":""},"AcidicPool10","Fewer resident fish thrive in nutrient-poor acidic ponds. Lakes and wetlands that are naturally acidic tend to have lower aquatic productivity and fewer fish species compared to non-acidic wetlands of the same size (Rahel 1984, Rago & Wiener 1986).  However, as pond size increases and ponds begin to resemble lakes, alkalinity often increases and consequently the ability to support a wider array of aquatic animals. Even where surrounded by bog vegetation and acidic soils with high DOC (Dissolved Organic Carbon) concentrations, many of these lakes are not acidic, especially when located low in a watershed (Eilers et al. 1993). In calculations, is excluded automatically (cell goes blank) if wetland is <0.01 ha.  If acidic ponded water is absent, the model ignores this indicator, but if present (\"1\"), the indicator score is set to zero. "]
[{"$f":"F!A102","v":"F22"},{"$f":"F!B102","v":"Fish"},{"$f":"F!C102","v":"Fish (native or stocked) are known to be present in the AA.  Or fish can access at least part of the AA during one or more days annually.  If uncertain, use answer from Form OF, item  OF15, or enter \"0\"."},{"$f":"F!D102","v":0},null,null,{"$f":"D79","v":0},"Fish10","Although simple presence of fish does not necessarily indicate optimal habitat, their presence suggests that habitat suitability is at least minimal. Is excluded from calculations (cell goes blank) automatically if wetland is <0.01 ha."]
[{"$f":"F!A103","v":"F23"},{"$f":"F!B103","v":"Beaver Probability"},{"$f":"F!C103","v":"Use of the AA by beaver during the past 5 years is (select most applicable ONE):"},null,null,null,{"$f":"MAX(F81:F84)/MAX(E81:E84)","v":0},"Beaver10","Over the long term, beaver dam-building activities are highly beneficial to fish rearing habitat, creating pools used by fish as refuge, adding wood that provides fish cover, and increasing the overall productivity of river systems (Murphy et al. 1989, Collen & Gibson 2001). "]
[null,null,{"$f":"F!C104","v":"evident from direct observation or presence of gnawed limbs, dams, tracks, dens, lodges, or extensive stands of water-killed trees (snags)."},{"$f":"F!D104","v":0},5,{"$f":"D81*E81","v":0}]
[null,null,{"$f":"F!C105","v":"likely based on known occurrence in the region and proximity to suitable habitat, which may include: (a) a persistent freshwater wetland, pond, or lake, or a perennial low or mid-gradient (<10%) channel, and (b) a corridor or multiple stands of hardwood trees and shrubs in vegetated areas near surface water."},{"$f":"F!D105","v":0},2,{"$f":"D82*E82","v":0}]
[null,null,{"$f":"F!C106","v":"unlikely because site characteristics above are deficient, and/or this is a settled area or other area where beaver are routinely removed.  But beaver occur in this part of the region (i.e., within 25 km)."},{"$f":"F!D106","v":0},1,{"$f":"D83*E83","v":0}]
[null,null,{"$f":"F!C107","v":"none.  Beaver are absent from this part of the region."},{"$f":"F!D107","v":0},0,{"$f":"D84*E84","v":0}]
[{"$f":"F!A109","v":"F25"},{"$f":"F!B109","v":"Through Flow Pattern"},{"$f":"F!C109","v":"During its travel through the AA at the time of peak annual flow, most of the water arriving in channels [select only the ONE encountered by most of the incoming water]:"},null,null,null,{"$f":"IF((Inflows=0),\"\",MAX(F86:F90)/MAX(E86:E90))","v":""},"ThruFlo10","Diffuse flow paths and large spatial complexity of channels within a wetland support a wider variety of microhabitats for fish and their invertebrate foods. "]
[null,null,{"$f":"F!C110","v":"Does not bump into plant stems as it travels through the AA.  Nearly all the water continues to travel in unvegetated (often incised) channels that have little contact with wetland vegetation, or through a zone of open water such as an instream pond or lake."},{"$f":"F!D110","v":0},1,{"$f":"D86*E86","v":0}]
[null,null,{"$f":"F!C111","v":"bumps into herbaceous vegetation but mostly remains in fairly straight channels."},{"$f":"F!D111","v":0},2,{"$f":"D87*E87","v":0}]
[null,null,{"$f":"F!C112","v":"bumps into herbaceous vegetation and mostly spreads throughout, or is in widely  meandering, multi-branched, or braided channels."},{"$f":"F!D112","v":0},4,{"$f":"D88*E88","v":0}]
[null,null,{"$f":"F!C113","v":"bumps into tree trunks and/or shrub stems but mostly remains in fairly straight channels."},{"$f":"F!D113","v":0},3,{"$f":"D89*E89","v":0}]
[null,null,{"$f":"F!C114","v":"bumps into tree trunks and/or shrub stems and follows a fairly indirect path from entrance to exit (meandering, multi-branched, or braided)"},{"$f":"F!D114","v":0},4,{"$f":"D90*E90","v":0}]
[{"$f":"F!A115","v":"F26"},{"$f":"F!B115","v":"Channel Connection & Outflow Duration"},{"$f":"F!C115","v":"The most persistent surface water connection (outlet channel or pipe, ditch, or overbank water exchange) between the AA and the closest off-site downslope water body is:"},null,null,null,{"$f":"MAX(F92:F96)/MAX(E92:E96)","v":0},"OutDura10","Fish access to wetlands is better if an outlet is present and outflows from the wetland are persistent. Although isolated wetlands with persistent surface water can support some resident fish, a permanent connection to other surface waters increases the ability of fish to move among wetlands and other surface waters in search of food and other needs.  "]
[null,null,{"$f":"F!C116","v":"persistent (>9 months/year, including times when frozen)"},{"$f":"F!D116","v":0},3,{"$f":"D92*E92","v":0}]
[null,null,{"$f":"F!C117","v":"seasonal (14 days to 9 months/year, not necessarily consecutive, including times when frozen)"},{"$f":"F!D117","v":0},2,{"$f":"D93*E93","v":0}]
[null,null,{"$f":"F!C118","v":"temporary (<14 days, not necessarily consecutive -- must be unfrozen)"},{"$f":"F!D118","v":0},1,{"$f":"D94*E94","v":0}]
[null,null,{"$f":"F!C119","v":"none -- but maps show a stream or other water body that is downslope from the AA and within a distance that is less than the AA's length.  If so, mark \"1\" here and SKIP TO F28 (Groundwater). "},{"$f":"F!D119","v":0},0,{"$f":"D95*E95","v":0}]
[null,null,{"$f":"F!C120","v":"no surface water flows out of the wetland except possibly during extreme events (<once per 10 years). Or, water flows only into a wetland, ditch, or lake that lacks an outlet.  If so, mark \"1\" here and SKIP TO F28 (Groundwater). "},{"$f":"F!D120","v":0},0,{"$f":"D96*E96","v":0}]
[{"$f":"F!A125","v":"F28"},{"$f":"F!B125","v":"Groundwater: Strength of Evidence"},{"$f":"F!C125","v":"Select first applicable choice. "},null,null,null,{"$f":"MAX(F98:F100)/MAX(E98:E100)","v":0},"Groundw10","Groundwater provides a relatively steady input of nutrients that supports algal production and the invertebrate foods important to resident fish. It also provides relatively warm temperatures that can maintain ice-free conditions for longer, and helps sustain water levels and low flows, thus increasing annual production. However, the \"flocs\" created by the presence of iron oxidizing bacteria in some instances causes groundwater to be deficient in oxygen that is critical to resident fish, especially when this occurs under winter ice cover.  "]
[null,null,{"$f":"F!C126","v":"Groundwater monitoring has demonstrated that groundwater primarily discharges to the wetland for longer periods during the year than periods when the wetland recharges the groundwater.  Or, springs are known to be present within the AA.\n\n\n"},{"$f":"F!D126","v":0},2,{"$f":"D98*E98","v":0}]
[null,null,{"$f":"F!C127","v":"One or more of the following are true: (a) the upper end of the AA is located very close to the base of (but mostly not ON) a natural slope much steeper (usually >15%) than that within the AA and longer than 100 m, OR\n(b) rust deposits (\"iron floc\"), colored precipitates, or dispersible natural oil sheen are prevalent in the AA, OR\n(c) AA water is remarkably clear in contrast to naturally stained waters typical in nearby wetlands, OR\n(d) AA is located at a geologic fault.\n\n"},{"$f":"F!D127","v":0},1,{"$f":"D99*E99","v":0}]
[null,null,{"$f":"F!C128","v":"Neither of above is true, although some groundwater may discharge to or flow through the AA.  Or groundwater influx is unknown."},{"$f":"F!D128","v":0},0,{"$f":"D100*E100","v":0}]
[{"$f":"F!A249","v":"F52"},{"$f":"F!B249","v":"Natural Cover in Buffer"},{"$f":"F!C249","v":"Along the wetland-upland edge and extending 30 m upslope, the percentage of the upland that contains natural (not necessarily native -- see column E) land cover taller than 10 cm is:"},null,null,null,{"$f":"MAX(F102:F106)/MAX(E102:E106)","v":0},"NatVegCUpct10","Streams adjoined by natural vegetation provide shade that helps maintain water temperature, as well as supporting richer and healthier communities of fish as well as invertebrates. Often, only very tolerant fish species are present in streams in heavily urbanized areas (Yoder et al. 1999) and invasive species may enjoy a competitive advantage over native species under urban conditions (Boet et al. 1999). "]
[null,null,{"$f":"F!C250","v":"<5% "},{"$f":"F!D250","v":0},0,{"$f":"D102*E102","v":0}]
[null,null,{"$f":"F!C251","v":"5 to 30%"},{"$f":"F!D251","v":0},2,{"$f":"D103*E103","v":0}]
[null,null,{"$f":"F!C252","v":"30 to 60%"},{"$f":"F!D252","v":0},3,{"$f":"D104*E104","v":0}]
[null,null,{"$f":"F!C253","v":"60 to 90%"},{"$f":"F!D253","v":0},4,{"$f":"D105*E105","v":0}]
[null,null,{"$f":"F!C254","v":">90%.  SKIP to F54 (Cliffs)."},{"$f":"F!D254","v":0},6,{"$f":"D106*E106","v":0}]
[{"$f":"F!A307","v":"F65"},{"$f":"F!B307","v":"Salinity, Alkalinity, Conductance "},{"$f":"F!C307","v":"Based on measurement from a surface water area larger than .01 hectare, the AA's surface water is mostly:"},null,null,null,{"$f":"IF((D111=1),\"\", IF((D108=1),0,\"\"))","v":""},"Salin10","Most native fish species in this region have low tolerance for highly saline waters.  If wetland is saline or brackish the score for this indicator is 0.  Otherwise it is ignored in the calculations and does not reduce the score."]
[null,null,{"$f":"F!C308","v":"Brackish or saline (conductance of >25 mS/cm, or >5000 ppm TDS). Or plants that indicate saline conditions comprise >20% of ground cover.  Trees and shrubs mostly absent.  Salt crust obvious around the perimeter and on flats."},{"$f":"F!D308","v":0},0]
[null,null,{"$f":"F!C309","v":"Slightly brackish (conductance of 2.5- 25 mS/cm, or 500 - 5000 ppm TDS).  Or plants that indicate saline conditions comprise 1-20% of ground cover.  Salt crust may or may not be present along perimeter."},{"$f":"F!D309","v":0},1]
[null,null,{"$f":"F!C310","v":"Fresh (conductance of < 2.5 mS/cm, or <500 ppm TDS). Plants that indicate saline conditions are sparse or absent. No salt crust along perimeter."},{"$f":"F!D310","v":0},2]
[null,null,{"$f":"F!C311","v":"Unknown condition (was not measured because surface water absent or insufficient, or measurement conflicted with plant indicators). "},{"$f":"F!D311","v":0}]
[{"$f":"F!A312","v":"F66"},{"$f":"F!B312","v":"Water Quality Problem Area Located Upslope"},{"$f":"F!C312","v":"Sampling indicates problems with the quality of surface waters or sediment within the AA, or within 5 km upstream or upslope, as caused by (enter 1 for ALL that apply):"},null,null,null,{"$f":"IF((D117=1),\"\",1-MAX(D113:D116))","v":1},"WQprob10","If water containing toxic substances enters a wetland, the wetland has much less capacity to support fish, or fish may be unsafe to consume. Resident fish are especially prone to bioaccumulation of locally-sourced metals (e.g., Deniseger et al. 1990). In calculations, is excluded automatically (cell goes blank) if wetland never has surface water during an average year."]
[null,null,{"$f":"F!C313","v":"nutrients (phosphorus, nitrate, ammonia), or a water body within 5 km that contributes to the AA has been labeled \"hyper-eutrophic\" based on excessive levels of either total phosphorus or chlorophyll-a."},{"$f":"F!D313","v":0}]
[null,null,{"$f":"F!C314","v":"suspended sediment or turbidity"},{"$f":"F!D314","v":0}]
[null,null,{"$f":"F!C315","v":"metals (mercury, lead, zinc, copper, cadmium, others)"},{"$f":"F!D315","v":0}]
[null,null,{"$f":"F!C316","v":"petrochemicals (pesticides, herbicides, PCBs, others)"},{"$f":"F!D316","v":0}]
[null,null,{"$f":"F!C317","v":"None of above, or no data. "},{"$f":"F!D317","v":0}]
[{"$f":"F!A328","v":"F69"},{"$f":"F!B328","v":"Plants or Animals of Conservation Concern"},{"$f":"F!C328","v":"If required, survey the AA for plant or animal species believed to be of conservation concern in Alberta (see list on Form F in Appendix A of Manual).  Do so at appropriate times of the year, especially if the data review conducted during the office phase of this assessment indicated their past presence in the general vicinity.  If you do detect these species or have reliable knowledge of their recent (within ~5 years) occurrence within the AA, indicate that below.  "},null,null,null,null,"RareFish","Because of their relative rarity, these fish species contribute more to regional biodiversity than fish species with broader habitat tolerances."]
[null,null,{"$f":"F!C330","v":"One or more of the rare fish species was detected within the AA."},{"$f":"F!D330","v":0},null,null,{"$f":"IF((D119=1),1,\"\")","v":""}]
[{"$f":"S!A3","v":"S5"},{"$f":"S!B3","v":"Altered Timing of Water Inputs"},{"$f":"S!E17","v":"Stressor Subscore="},{"$f":"S!F17","v":0},null,null,{"$f":"IF((AllSat+AllSat1>0),\"\",1-(D120/5))","v":1},"AltTime10","Life histories of resident fish are closely synchronized to natural hydrologic patterns. Wetlands where that has been disrupted will have lower capacity to support resident fish. In calculations, is excluded automatically (cell goes blank) if wetland never has surface water during an average year."]
[{"$f":"S!A18","v":"S6"},{"$f":"S!B18","v":"Accelerated Inputs of Contaminants and/or Salts"},null,{"$f":"S!D18","v":0},null,null,{"$f":"1-D121","v":1},"Toxic10","Presence of contaminant sources suggests the potential for long-term harm to fish populations (e.g., Jeffries et al. 2008a,b, Brinkmann 2012, Brinkmann & Rasmussen 2012)."]
[]
[null,null,"Productivity [CfixF]"]
[null,null,"AVERAGE(GrowDD, Spring, Groundw10, Wettype10, Lake10, MAX(FishPres, Fish10), Fringe10, Salin10, Beaver, AcidicPool10)",null,null,null,{"$f":"IFERROR(AVERAGE(GrowDD, Spring, Groundw10, Wettype10, Lake10, MAX(FishPres, Fish10), Fringe10, Salin10, Beaver10, AcidicPool10),\"\")","v":0}]
[]
[null,null,"Water Permanence [Water]"]
[null,null,"AVERAGE(WatProb, OutDura10, PermWpct10, SatPct10)  ",null,null,null,{"$f":"IFERROR(AVERAGE(WatProb, OutDura10, PermWpct10, SatPct10),\"\")","v":0}]
[]
[null,null,"Habitat Structure [HabStrucF]"]
[null,"Wetlands <10 hectares:","AVERAGE(Interspers10, ThruFlo10, Depth10, DepthEven10, Shade10, WoodAbove10)",null,null,null,{"$f":"IF((GT10HA=1),G131, IFERROR(IF((AllSat+AllSat>0),\"\",IF((SmallAA=1),\"\",AVERAGE(Interspers10, ThruFlo10, Depth10, DepthEven10, Shade10, WoodAbove10 ))),\"\"))","v":0}]
[null,"Wetlands >10 hectares:","Substituted MixWaterVeg",null,null,null,{"$f":"IFERROR(IF((AllSat+AllSat>0),\"\",IF((SmallAA=1),\"\",AVERAGE(MixWaterVeg, ThruFlo10, Depth10, DepthEven10, Shade10, WoodAbove10 ))),\"\")","v":0}]
[]
[null,null,"Avoidance of Anoxia [AnoxF]"]
[null,"Wetlands <10 hectares:","AVERAGE(1-Sub0Days, WetArea, RipFloodpl, OutDura10, Depth10, IsoDry10, OWpct10)",null,null,null,{"$f":"IF((GT10HA=1),G135, IFERROR(AVERAGE(Sub0Days, WetArea, OutDura10, RipFloodpl, Depth10, ISOdry10, OWpct10),\"\"))","v":0}]
[null,"Wetlands >10 hectares:","Substituted OWpct",null,null,null,{"$f":"IFERROR(AVERAGE(Sub0Days, WetArea,  OutDura10, RipFloodpl, Depth10, ISOdry10, OWpct),\"\")","v":0}]
[]
[null,null,"Avoidance of Other Stressors [StressF]"]
[null,null,"AVERAGE(Dist2Road,1-RdDens1k,PerimNatCov,1-WQrisk, Toxic10, WQprob10, AltTime10, NatVegCUpct10)",null,null,null,{"$f":"IFERROR(AVERAGE(Dist2Road,1-RdDens1k,PerimNatCov,1-WQrisk, Toxic10, WQprob10, AltTime10, NatVegCUpct10),\"\")","v":0.83333333333333337}]
[]
[null,null,"ABWRET-A FUNCTION MODEL"]
[null,null,"Fish Habitat"]
[null,null,"IF((RareFish=1),10, IF((AllSat+Fish10=0),0, IF((TooSaline + Fish10=0),0, ELSE: AVERAGE(CfixF, HabStrucF, Water, AnoxF, StressF)",null,null,null,{"$f":"IF((RareFish=1),10, IF((AllSat + (1-Fish10=1)),0, IF((TooSaline + (1-Fish10=1)),0, 10*AVERAGE(CfixF1a, HabStrucF1a, Water1a, AnoxF1a, StressF1a))))","v":0}]
[null,null,null,{"$f":"IFERROR(AVERAGE(FishPres, ChannConn, RipFloodpl),\"\")","v":""},null,null,null,null,"Literature Cited"]
[null,null,"ABWRET-E model",null,null,null,null,null,"Boët, P., Belliard J, Berrebi, T.R. 1999. Multiple human impacts by the City of Paris on fish communities in the Seine River Basin, France. Hydrobiologia 410:59-68."]
[null,1,"Calculate these averages:",null,null,null,null,null,"Brinkmann, L. and J. B. Rasmussen. 2010. High levels of mercury in biota of a new Prairie irrigation reservoir with a simplified food web in Southern Alberta, Canada. Hydrobiologia 641:11-21."]
[null,"a","AVERAGE(FishPres, RipFloodpl, ChanConn)",null,null,null,null,null,"Brinkmann, L. and J. B. Rasmussen. 2012. Elevated mercury levels in biota along an agricultural land use gradient in the Oldman River basin, Alberta. Canadian Journal of Fisheries and Aquatic Sciences 69:1202-1213."]
[null,"b","AVERAGE((WetArea-WetVegArea), 1-Sub0Days)",{"$f":"IFERROR(AVERAGE(1-Sub0Days, (WetArea-WetVegArea)),\"\")","v":0.5},null,null,null,null,"Collen, P. and R. J. Gibson. 2001. The general ecology of beavers (Castor spp.), as related to their influence on stream ecosystems and riparian habitats, and the subsequent effects on fish – a review. Reviews in Fish Biology and Fisheries 10:439–461."]
[null,"c","AVERAGE (OWpct, MixWaterVeg)",{"$f":"IFERROR(AVERAGE(OWpct, MixWaterVeg),\"\")","v":""},null,null,null,null,"Deniseger, J., L. J. Erickson, A. Austin, M. Roch, and M. J. R. Clark. 1990. The effects of decreasing heavy metal concentrations on the biota of Buttle Lake, Vancouver Island, British Columbia. Water Resources Bulletin 24:403-416."]
[null,"d","AVERAGE (DistRd, 1-RdDens1k, PerimNatCov)",{"$f":"IFERROR(AVERAGE(Dist2Road, 1-RdDens1k, PerimNatCov),\"\")","v":1},null,null,null,null,"Eilers, J. M., D. H. Landers, A. D. Newell, M. E. Mitch, M. Morrison, and J. Ford. 1993. Major Ion Chemistry of Lakes on the Kenai Peninsula, Alaska. Canadian Journal of Fisheries and Aquatic Sciences 50:816-826."]
[null,2,"10*AVERAGE(a, b, c, d, WatProb)",{"$f":"10*AVERAGE(WatProb,D143:D149)","v":7.5},null,null,null,null,"Jeffries, K. M., E. R. Nelson, L. J. Jackson, and H. R. Habibi. 2008. Basin-wide impacts of compounds with estrogen-like activity on longnose dace (Rhinichthys cataractae) in two prairie rivers of Alberta, Canada. Environmental Toxicology and Chemistry 27:2042-2052."]
[null,null,null,null,null,null,null,null,"Murphy, M. L., J. Heifetz, J. F. Thedinga, S. W. Johnson, and K. V. Koski. 1989. Habitat utilization by juvenile pacific salmon (Onchorynchus) in the glacial Taku River, Southeast Alaska. Canadian Journal of Fisheries and Aquatic Sciences 46:1677-1685."," "]
[null,null,"ABWRET-E with substitutions:",null,null,null,null,null,"Wipfli, M. S. and J. Musslewhite. 2004. Density of red alder (Alnus rubra) in headwaters influences invertebrate and detritus subsidies to downstream fish habitats in Alaska. Hydrobiologia 520:153-163."]
[null,1,"Calculate these averages:",null,null,null,null,null,"Wipfli, M. S., J. S. Richardson, and R. J. Naiman. 2007. Ecological linkages between headwaters and downstream ecosystems: Transport of organic matter, invertebrates, and wood down headwater channels. Journal of the American Water Resources Association 43:72-85. "]
[null,"a","AVERAGE(FishPres, RipFloodpl, OutDura10)",{"$f":"IFERROR(AVERAGE(FishPres, RipFloodpl, OutDura10),\"\")","v":0},null,null,null,null,"Yoder, C. O., R. J. Miltner, and D. White. 1999. Assessing the Status of Aquatic Life Designated Uses in Urban and Suburban Watersheds. Pages 16-28 in A. Everson et al., editor. Proceedings of National Conference on Retrofit Opportunities for Water Resource Protection in Urban Environments. Chicago, IL February 9-12, 1998. Technology Transfer and Support Division, National Risk Management Research Laboratory, Office of Research and Development, U.S. Environmental Protection Agency, Cincinnati, Ohio."]
[null,"b","AVERAGE((WetArea-WetVegArea), 1-Sub0Days)",{"$f":"IFERROR(AVERAGE(1-Sub0Days, (WetArea-WetVegArea)),\"\")","v":0.5}]
[null,"c","AVERAGE (OWpct10, Interspers10)",{"$f":"IFERROR(IF((AllSat+AllSat>0),\"\",IF((SmallAA=1),\"\", AVERAGE(OWpct10, Interspers10))),\"\")","v":0}]
[null,"d","AVERAGE (DistRd, 1-RdDens1k, PerimNatCov)",{"$f":"IFERROR(AVERAGE(Dist2Road, 1-RdDens1k, PerimNatCov),\"\")","v":1}]
[null,2,"10*AVERAGE(a, b, c, d, WatProb)",{"$f":"10*AVERAGE(WatProb,D154:D157)","v":3.75}]
[null,null,null,null,null,null," "]

{"sheet":"INV","index":17,"n_rows":196,"n_cols":12,"rows_kept":196,"cut":false,"hidden":false,"merged":[[0,4,0,8],[0,0,0,1],[27,0,33,0],[34,0,40,0],[16,1,20,1],[34,1,40,1],[27,1,33,1],[21,0,26,0],[16,7,20,7],[21,7,26,7],[27,7,33,7],[27,8,33,8],[16,8,20,8],[21,8,26,8],[34,8,40,8],[34,7,40,7],[128,0,130,0],[97,1,102,1],[73,1,76,1],[131,0,136,0],[94,0,96,0],[119,0,121,0],[122,1,127,1],[115,1,118,1],[122,0,127,0],[73,0,76,0],[97,0,102,0],[79,0,84,0],[115,0,118,0],[89,0,93,0],[119,1,121,1],[85,1,88,1],[73,8,76,8],[109,0,114,0],[94,8,96,8],[103,0,108,0],[103,1,108,1],[97,8,102,8],[94,1,96,1],[109,7,114,7],[109,1,114,1],[85,0,88,0],[85,8,88,8],[89,7,93,7],[97,7,102,7],[103,7,108,7],[85,7,88,7],[94,7,96,7],[47,0,51,0],[52,0,57,0],[79,8,84,8],[79,1,84,1],[41,1,46,1],[41,0,46,0],[47,1,51,1],[62,0,68,0],[58,1,61,1],[52,1,57,1],[58,8,61,8],[58,0,61,0],[69,0,72,0],[62,8,68,8],[69,7,72,7],[73,7,76,7],[52,8,57,8],[41,8,46,8],[47,8,51,8],[69,1,72,1],[21,1,26,1],[69,8,72,8],[122,7,127,7],[128,7,130,7],[41,7,46,7],[47,7,51,7],[52,7,57,7],[58,7,61,7],[79,7,84,7],[131,7,136,7],[109,8,114,8],[62,7,68,7],[62,1,68,1],[131,8,136,8],[131,1,136,1],[128,1,130,1],[89,1,93,1],[89,8,93,8],[119,8,121,8],[115,8,118,8],[103,8,108,8],[122,8,127,8],[128,8,130,8],[115,7,118,7],[119,7,121,7]]}
["Invertebrate Habitat",null,"The capacity to support or contribute to an abundance or diversity of invertebrate animals which spend all or part of their life cycle underwater or in moist soil.  Includes dragonflies, midges, clams, snails, water beetles, shrimp, aquatic worms, and others.\n","INV"]
["#","Function Indicators from Estimator","Scoring Notes",null,null,null,"Normalised Score","Indicator Abbreviation or Formula","Rationale"]
[{"$f":"OF!A6","v":"OF5"},{"$f":"OF!C6","v":"Wetland Class Richness Within 1km"}," ",null,null,null,{"$f":"IF((ClassRich1k=\"\"),\"\",ClassRich1k)","v":""},"ClassRich1k","Because different wetland classes are likely to have distinctive invertebrate assemblages, a greater variety of wetland classes implies greater invertebrate diversity."]
[{"$f":"OF!A7","v":"OF6"},{"$f":"OF!C7","v":"Wetland Class Richness Within Wetland"}," ",null,null,null,{"$f":"IF((ClassRichIn=\"\"),\"\",ClassRichIn)","v":""},"ClassRichIn","See above."]
[{"$f":"OF!A18","v":"OF17"},{"$f":"OF!C18","v":"Growing Degree Days"}," ",null,null,null,{"$f":"IF((GrowDD=\"\"),\"\",GrowDD)","v":""},"GrowDD","Plants are more productive at warmer soil or sediment temperatures, and this supports higher productivity of aquatic insects."]
[{"$f":"OF!A24","v":"OF23"},{"$f":"OF!C24","v":"% of the AA that is Marsh"},null,null,null,null,{"$f":"IF((MarshPct=\"\"),\"\",MarshPct)","v":""},"MarshPct","Wetlands classified as marsh (and perhaps fen) tend to have the most diverse assemblages of aquatic invertebrates."]
[{"$f":"OF!A25","v":"OF24"},{"$f":"OF!C25","v":"MarshPct/ MarshPct1k"}," ",null,null,null,{"$f":"IF((MarshUniq=\"\"),\"\",MarshUniq)","v":""},"MarshUniq","If a wetland contains marsh but marsh (which may be the most important class for invertebrates) is scarce in the surrounding area, the contribution of marsh-associated invertebrate species to local biodiversity is likely to be greater."]
[{"$f":"OF!A27","v":"OF26"},{"$f":"OF!C27","v":"Interspersion Index for Internal Herbaceous & Woody Vegetation (macroscale)"},null,null,null,null,{"$f":"IF((MixHerbWood=\"\"),\"\",MixHerbWood)","v":""},"MixHerbWood","Because woody and herbaceous vegetation are likely to have different invertebrate assemblages, the well-distributed interspersion of both in a wetland implies greater invertebrate diversity."]
[{"$f":"OF!A28","v":"OF27"},{"$f":"OF!C28","v":"Interspersion Index for Internal Water & Vegetation (macroscale)"}," ",null,null,null,{"$f":"IF((MixWaterVeg=\"\"),\"\",MixWaterVeg)","v":""},"MixWaterVeg","Interspersion of relatively equal-sized patches of open water and vegetation provides habitat for both open-water invertebrate species and those that mostly live among plants."]
[{"$f":"OF!A29","v":"OF28"},{"$f":"OF!C29","v":"% Natural Cover within 1km"}," ",null,null,null,{"$f":"IF((NatCov1k=\"\"),\"\",NatCov1k)","v":""},"NatCov1k","Aquatic macroinvertebrate communities are negatively associated with agricultural land in a catchment but positively associated with forested land or other perennial cover in areas closest to a stream or wetland (Steedman 1988, Wang et al. 1997).\n\n"]
[{"$f":"OF!A32","v":"OF31"},{"$f":"OF!C32","v":"% of AA that is Open Water (macro scale, Invertebrate Habitat)"},"The raw value is scored as follows: <1%=0.2;  1%-5%=0.6; 6-30%=0.8, 31-70%=1; 71-99%=0.4; >99%=0. ",null,null,null,{"$f":"IF((OWpct_INV=\"\"),\"\",OWpct_INV)","v":""},"OWpct_INV","See above."]
[{"$f":"OF!A35","v":"OF34"},{"$f":"OF!C35","v":"% of Wetland Perimeter Adjoined by Natural Cover"}," ",null,null,null,{"$f":"IF((PerimNatCov=\"\"),\"\",PerimNatCov)","v":""},"PerimNatCov","Densities of freshwater shrimp in prairie wetlands are greater in wetlands surrounded with upland perennial vegetation (Anteau et al. 2011).  However,  another study in prairie wetlands found that invertebrate densities and richness were not strongly related to the surrounding land use (Tangen et al. 2003)."]
[{"$f":"OF!A51","v":"OF50"},{"$f":"OF!C51","v":"Springs within 300m"},"If wetland lacks a spring then ignored (NULL) in calculations rather than reducing the score.",null,null,null,{"$f":"IF((Spring=\"\"),\"\",IF((Spring=1),1,\"\"))","v":""},"Spring","Springs are widely known to host invertebrate species found in few or no other habitats (Brown 2007)."]
[{"$f":"OF!A61","v":"OF60"},{"$f":"OF!C61","v":"Water Permanence Probability"}," ",null,null,null,{"$f":"IF((WatProb=\"\"),\"\",WatProb)","v":""},"WatProb","The probability of surface water occurring is presumed correlated with the seasonal persistence of surface water.  Wetlands in which surface water persists longer are capable of supporting a wider variety of invertebrates, e.g., those that require many months or years to complete their life cycle, as well as those that mature more rapidly. "]
[{"$f":"OF!A73","v":"OF72"},{"$f":"OF!C73","v":"Surface Water Quality Risk Index"},"Inverse",null,null,null,{"$f":"IF((WQrisk=\"\"),\"\",1-WQrisk)","v":""},"WQrisk","Some invertebrates, such as amphipods, are highly sensitive to pesticides used on crops (Morrill & Neal 1990, Goldsborough & Crumpton 1998, Donald et al. 1999), and invertebrates are harmed by many other pollutants.  "]
["#","Function Indicators from Onsite Visit","Categorical Choices","Data","Weight","Data  x  Weight","Normalised Score","Indicator Abbreviation or Formula","Rationale & Scoring Notes"]
[{"$f":"F!A6","v":"F1"},{"$f":"F!B6","v":"Wetland Type - Predominant"},{"$f":"F!C6","v":"Most of the vegetated part of the AA (wetland Assessment Area) is a (select ONE):"},null,null,null,{"$f":"MAX(F18:F21)/MAX(E18:E21)","v":0},"Wettype8","Many invertebrate groups (e.g., snails, isopods, lumbricid worms) cannot tolerate acidic conditions of bogs, and invertebrate richness generally tends to be greater in persistently inundated fens than in less persistently inundated marshes with more mineral soils (Holmquist et al. 2011).  However, marshes along lakes and rivers tend to have water longer into the growing season than other marshes and can support high abundance and diversity of invertebrates. One study reported that bogs and fens did not differ significantly with regard to invertebrate faunas. Dragonflies seemed to respond to the habitat's form and structure more than to its acidity or nutrient levels (Cannings & Cannings 1994)"]
[{"$f":"F!A7","v":"F1.1"},null,{"$f":"F!C7","v":"Wooded Swamp"},{"$f":"F!D7","v":0},3,{"$f":"D18*E18","v":0}]
[{"$f":"F!A8","v":"F1.2"},null,{"$f":"F!C8","v":"Bog"},{"$f":"F!D8","v":0},1,{"$f":"D19*E19","v":0}]
[{"$f":"F!A9","v":"F1.3"},null,{"$f":"F!C9","v":"Fen"},{"$f":"F!D9","v":0},5,{"$f":"D20*E20","v":0}]
[{"$f":"F!A10","v":"F1.4"},null,{"$f":"F!C10","v":"Marsh or Shallow Open Water"},{"$f":"F!D10","v":0},6,{"$f":"D21*E21","v":0}]
[{"$f":"F!A11","v":"F2"},{"$f":"F!B11","v":"Wetland Types - Subordinate"},{"$f":"F!C11","v":"Mark all other vegetated wetland types in the AA that occupy more than 1 hectare or more than 1% of the vegetated AA.  Do not mark the predominant type again.  If AA is larger than 1 ha, see preliminary imagery-based answer provided by AESRD, but field-verify."},null,null,null,{"$f":"SUM(D23:D26)/4","v":0},"ClassRichIn8","see above.  The score is the number of classes marked here divided by 4."]
[null,null,{"$f":"F!C12","v":"Wooded Swamp"},{"$f":"F!D12","v":0}]
[null,null,{"$f":"F!C13","v":"Bog"},{"$f":"F!D13","v":0}]
[null,null,{"$f":"F!C14","v":"Fen"},{"$f":"F!D14","v":0}]
[null,null,{"$f":"F!C15","v":"Marsh or Shallow Open Water"},{"$f":"F!D15","v":0}]
[null,null,{"$f":"F!C16","v":"no types other than the predominant one in F1 meet the area threshold."},{"$f":"F!D16","v":0}]
[{"$f":"F!A17","v":"F3"},{"$f":"F!B17","v":"% Saturated Only"},{"$f":"F!C17","v":"The percentage of the AA that never contains surface water during an average year (that is, except perhaps for a few hours after snowmelt or rainstorms), but which is still a wetland, is:"},null,null,null,{"$f":"MAX(F29:F34)/MAX(E29:E34)","v":0},"SatPct8","The larvae of many wetland invertebrates require surface water, so the absence or scarcity of that limits aquatic invertebrate richness."]
[null,null,{"$f":"F!C18","v":"less than 1%, or <0.01 hectare (about 10 m on a side) never has surface water.  In other words, all or nearly all of the AA is inundated permanently or at least seasonally."},{"$f":"F!D18","v":0},5,{"$f":"D29*E29","v":0}]
[null,null,{"$f":"F!C19","v":"1-25% of the AA never contains surface water."},{"$f":"F!D19","v":0},6,0]
[null,null,{"$f":"F!C20","v":"25-50% of the AA never contains surface water."},{"$f":"F!D20","v":0},4,0]
[null,null,{"$f":"F!C21","v":"50-99% of the AA never contains surface water."},{"$f":"F!D21","v":0},3,0]
[null,null,{"$f":"F!C22","v":">99% of the AA never contains surface water, except for water flowing in channels and/or in pools that occupy <1% of the AA. SKIP to F26 (Channel Connection & Outflow Duration)"},{"$f":"F!D22","v":0},2,0]
[null,null,{"$f":"F!C23","v":">99% of the AA never contains surface water, and AA is not intersected by channels that have flow, not even for a few days per year. SKIP to F26."},{"$f":"F!D23","v":0},1,0]
[{"$f":"F!A24","v":"F4"},{"$f":"F!B24","v":"% with Persistent Surface Water"},{"$f":"F!C24","v":"The percentage of the AA that has surface water (either ponded or flowing, either open or obscured by vegetation) during all of the growing season during most years is:"},null,null,null,{"$f":"IF((AllSat+AllSat>0),\"\",MAX(F36:F41)/MAX(E36:E41))","v":0},"PermWpct8","Wetlands in which surface water persists longer are capable of supporting a wider variety of invertebrates, e.g., those that require many months or years to complete their life cycle, as well as those that mature more rapidly. Thus, wetlands with a proportionately large extent of persistent water may benefit a wide range of aquatic invertebrates.  However, even wetlands that remain dry for years before reflooding can support aquatic invertebrates that have dormant eggs that remain viable during drought.  Reflooded wetlands also are quickly recolonised by flying aquatic insects. In calculations, is excluded automatically (cell goes blank) if wetland never has surface water during an average year. "]
[null,null,{"$f":"F!C25","v":"less than 1%, or <0.01 hectare (whichever is less).  SKIP to F8 (% Flooded Only Seasonally)."},{"$f":"F!D25","v":0},0,{"$f":"D36*E36","v":0}]
[null,null,{"$f":"F!C26","v":"1-25% of the AA, and mostly in narrow channels and/or small scattered pools."},{"$f":"F!D26","v":0},1,0]
[null,null,{"$f":"F!C27","v":"1-25% of the AA, and mostly in a single large pool, pond, and/or channel."},{"$f":"F!D27","v":0},2,0]
[null,null,{"$f":"F!C28","v":"25-50% of the AA"},{"$f":"F!D28","v":0},2,0]
[null,null,{"$f":"F!C29","v":"50-95% of the AA"},{"$f":"F!D29","v":0},3,0]
[null,null,{"$f":"F!C30","v":">95% of the AA"},{"$f":"F!D30","v":0},4,0]
[{"$f":"F!A39","v":"F8"},{"$f":"F!B39","v":"% Flooded Only Seasonally"},{"$f":"F!C39","v":"The percentage of the AA that is covered by surface water only during the wettest time of year (and for >2 consecutive days during that time) is:"},null,null,null,{"$f":"IF((AllSat+AllSat>0),\"\",MAX(F43:F47)/MAX(E43:E47))","v":0},"SeasPct8","The parts of a wetland that are inundated only seasonally may contain water long enough for many invertebrates to complete their life cycle, while providing fresh food resources (e.g., plant litter). They also tend to be shallower and less deficient in dissolved oxygen, making them suitable for a wider range of species. Seasonal fluctuations release nutrients bound up in wetland sediments, and stimulate the growth of new plants whose seeds have been dormant.  However, some invertebrate taxa, such as those without winged adult stages living in isolated wetlands (bog pools), may not survive prolonged desiccation. In calculations, is excluded automatically (cell goes blank) if wetland never has surface water during an average year."]
[null,null,{"$f":"F!C40","v":"<1%. "},{"$f":"F!D40","v":0},3,{"$f":"D43*E43","v":0}]
[null,null,{"$f":"F!C41","v":"1-25% "},{"$f":"F!D41","v":0},4,{"$f":"D44*E44","v":0}]
[null,null,{"$f":"F!C42","v":"25-50% "},{"$f":"F!D42","v":0},3,{"$f":"D45*E45","v":0}]
[null,null,{"$f":"F!C43","v":"50-95% "},{"$f":"F!D43","v":0},2,{"$f":"D46*E46","v":0}]
[null,null,{"$f":"F!C44","v":">95% "},{"$f":"F!D44","v":0},1,{"$f":"D47*E47","v":0}]
[{"$f":"F!A45","v":"F9"},{"$f":"F!B45","v":"Annual Water Fluctuation Range"},{"$f":"F!C45","v":"The annual fluctuation in surface water level within most of the parts of the AA that contain surface water is:"},null,null,null,{"$f":"IF((AllSat+AllSat>0),\"\",IF((NoSeasonal=1),\"\",MAX(F49:F52)/MAX(E49:E52)))","v":0},"Fluctu8","Dynamic water levels in wetlands with outlets usually imply more productive wetlands (Nicholson 1995). However, if water level fluctuations are too severe (e.g., greater than plant height) production of organic matter can diminish. Also, more stable water levels may benefit aquatic invertebrates in regions where many streams and wetlands are prone to sudden fluctuations from melting snow and storms. In calculations, is excluded automatically (cell goes blank) if wetland never has surface water during an average year, or if none of it floods only seasonally."]
[null,null,{"$f":"F!C46","v":"<10 cm change (stable) "},{"$f":"F!D46","v":0},3,{"$f":"D49*E49","v":0}]
[null,null,{"$f":"F!C47","v":"10 cm - 50 cm change"},{"$f":"F!D47","v":0},4,{"$f":"D50*E50","v":0}]
[null,null,{"$f":"F!C49","v":"1-2 m change"},{"$f":"F!D49","v":0},2,{"$f":"D51*E51","v":0}]
[null,null,{"$f":"F!C50","v":">2 m change"},{"$f":"F!D50","v":0},1,{"$f":"D52*E52","v":0}]
[{"$f":"F!A52","v":"F10"},{"$f":"F!B52","v":"Predominant Depth Class"},{"$f":"F!C52","v":"During most of the time when water is present, its depth in most of the area is: [Note: This is not asking for the maximum depth.]"},null,null,null,{"$f":"IF((AllSat+AllSat>0),\"\", IF((SmallAA=1),\"\", MAX(F54:F58)/MAX(E54:E58)))","v":0},"Depth8","Provided that they hold surface water for several weeks, shallow areas support greater primary production, support higher vascular plant densities, and consequently greater invertebrate production. In calculations, is excluded automatically (cell goes blank) if wetland never has surface water during an average year. Also is excluded automatically if wetland is <0.01 ha."]
[null,null,{"$f":"F!C53","v":"<10 cm deep (but >0)"},{"$f":"F!D53","v":0},3,{"$f":"D54*E54","v":0}]
[null,null,{"$f":"F!C54","v":"10 - 50 cm deep"},{"$f":"F!D54","v":0},5,{"$f":"D55*E55","v":0}]
[null,null,{"$f":"F!C55","v":"0.5 - 1 m deep"},{"$f":"F!D55","v":0},4,{"$f":"D56*E56","v":0}]
[null,null,{"$f":"F!C56","v":"1 - 2 m deep"},{"$f":"F!D56","v":0},2,{"$f":"D57*E57","v":0}]
[null,null,{"$f":"F!C57","v":">2 m deep.  True for many fringe wetlands."},{"$f":"F!D57","v":0},1,{"$f":"D58*E58","v":0}]
[{"$f":"F!A58","v":"F11"},{"$f":"F!B58","v":"Depth Classes - Evenness of Proportions"},{"$f":"F!C58","v":"When present, surface water in most of the AA usually consists of (select one):"},null,null,null,{"$f":"IF((AllSat+AllSat>0),\"\", IF((SmallAA=1),\"\", MAX(F60:F62)/MAX(E60:E62)))","v":0},"DepthDiv8","Different invertebrate groups thrive at different water depths in boreal wetlands (Corcoran et al. 2009). Thus, a variety of depths may promote greater invertebrate richness for the wetland as a whole. In calculations, is excluded automatically (cell goes blank) if wetland never has surface water during an average year. Also is excluded automatically if wetland is <0.01 ha."]
[null,null,{"$f":"F!C59","v":"One depth class that comprises >90% of the AA’s inundated area (use the classes in the question above)."},{"$f":"F!D59","v":0},0,{"$f":"D60*E60","v":0}]
[null,null,{"$f":"F!C60","v":"One depth class that comprises 60-90% of the AA's inundated area."},{"$f":"F!D60","v":0},1,{"$f":"D61*E61","v":0}]
[null,null,{"$f":"F!C61","v":"Neither of above.  Multiple depth classes; none occupy more than 50% of the AA."},{"$f":"F!D61","v":0},2,{"$f":"D62*E62","v":0}]
[{"$f":"F!A71","v":"F14"},{"$f":"F!B71","v":"% of Ponded Water That Is Open "},{"$f":"F!C71","v":"In ducks-eye aerial view, the percentage of the ponded water that is open (lacking emergent vegetation during most of the growing season, and unhidden by a forest or shrub canopy) is:"},null,null,null,{"$f":"IF((AllSat+AllSat>0),\"\",IF((NoPonded=1),\"\", IF((SmallAA=1),\"\", MAX(F64:F69)/MAX(E64:E69))))","v":0},"OWpct8","Emergent and submerged vegetation typically hosts extensive growths of epiphytic algae, which along with the supporting herbaceous plants, provide food and cover for a wide variety of invertebrates.  Intermediate cover conditions allow more light penetration of the water column, higher algal productivity, greater oxygenation, and thus tend to support a wide variety of invertebrate groups. In calculations, is excluded automatically (cell goes blank) if wetland never has surface water during an average year or has no ponded water or is <0.01 ha."]
[null,null,{"$f":"F!C72","v":"<1% or none, or largest pool occupies <0.01 hectares.  Enter \"1\" and SKIP to F20 (Floating Algae & Duckweed)."},{"$f":"F!D72","v":0},1,{"$f":"D64*E64","v":0}]
[null,null,{"$f":"F!C73","v":"1-5% of the ponded water.  Enter \"1\" and SKIP to F20."},{"$f":"F!D73","v":0},3,0]
[null,null,{"$f":"F!C74","v":"5-30% of the ponded water."},{"$f":"F!D74","v":0},4,0]
[null,null,{"$f":"F!C75","v":"30-70% of the ponded water."},{"$f":"F!D75","v":0},6,0]
[null,null,{"$f":"F!C76","v":"70-99% of the ponded water."},{"$f":"F!D76","v":0},2,0]
[null,null,{"$f":"F!C77","v":"100% of the ponded water. "},{"$f":"F!D77","v":0},0,0]
[{"$f":"F!A91","v":"F17"},{"$f":"F!B91","v":"Non-vegetated Aquatic Cover"},{"$f":"F!C91","v":"Near waters that are deeper than 0.5 m, the cover for fish, aquatic invertebrates, and/or amphibians that is provided by horizontally incised banks and/or partly-submerged accumulations of wood thicker than 10 cm (NOT by living vegetation) is:"},null,null,null,{"$f":"IF((AllSat+AllSat>0),\"\",IF((OpenW=0),\"\", IF((SmallAA=1),\"\", MAX(F71:F73)/MAX(E71:E73))))","v":""},"AqCov8","The importance of large wood to aquatic life has been widely documented in perennial streams (literature reviewed by Murphy 1995, May 2003, Wenger 2000) and in lakes (Roth et al. 2007). Many aquatic invertebrates attach to submerged wood and feed on algae and leaves associated with it. Constructed wetlands to which woody debris is added may support greater biomass or richness of several aquatic invertebrate groups (e.g., Alsfeld et al. 2009). Most instream wood originates in the parts of the riparian areas that are within 100 ft of a stream (McDade et al. 1990, Van Sickle & Gregory 1990, Robison & Beschta 1990, Meleason et al. 2003). In calculations, is excluded automatically (cell goes blank) if wetland never has surface water during an average year, or has no open water, or  is <0.01 ha."]
[null,null,{"$f":"F!C92","v":"Little or none, or all water is shallower than 0.5 m most of the year."},{"$f":"F!D92","v":0},0,{"$f":"D71*E71","v":0}]
[null,null,{"$f":"F!C93","v":"Intermediate"},{"$f":"F!D93","v":0},1,{"$f":"D72*E72","v":0}]
[null,null,{"$f":"F!C94","v":"Extensive"},{"$f":"F!D94","v":0},2,{"$f":"D73*E73","v":0}]
[{"$f":"F!A95","v":"F18"},{"$f":"F!B95","v":"Interspersion of Robust Emergents & Open Water"},{"$f":"F!C95","v":"During most of the growing season, the spatial pattern of tall robust herbaceous vegetation (e.g., cattail, bulrush) that has surface water beneath it is mostly:"},null,null,null,{"$f":"IF((AllSat+AllSat>0),\"\",IF((NoPonded=1),\"\",IF((NoOpenPonded+NoOpenPonded1>0),\"\",IF((AllOpenPond=1),\"\", IF((SmallAA=1),\"\", MAX(F75:F77)/MAX(E75:E77))))))","v":0},"Interspers8","Greater invertebrate diversity overall may be supported by wetlands with a relatively even mix of open water and vegetation, interspersed throughout. Such conditions reflect a variety of light, temperature, and oxygen regimes as well as edge habitats (ecotones) that together provide more niches for invertebrates. In calculations, is excluded automatically (cell goes blank) if wetland never has surface water during an average year, if no ponded water, if ponded water but no vegetation, if ponded but no open water, or if <0.01 ha."]
[null,null,{"$f":"F!C96","v":"Scattered in small clumps, islands, or patches throughout the surface water area."},{"$f":"F!D96","v":0},3,{"$f":"D75*E75","v":0}]
[null,null,{"$f":"F!C97","v":"Intermediate"},{"$f":"F!D97","v":0},2,{"$f":"D76*E76","v":0}]
[null,null,{"$f":"F!C98","v":"Clumped at one or a few sides of the surface water area, or mostly surrounds a central area of open water.  Or such vegetation is absent or covers <9 sq m and <1% of the AA."},{"$f":"F!D98","v":0},1,{"$f":"D77*E77","v":0}]
[{"$f":"F!A101","v":"F21"},{"$f":"F!B101","v":"Stained Surface Water"},{"$f":"F!C101","v":"Most surface water is tea-colored (from tannins, not iron bacteria or silt), and/or its pH is usually <5.5. Nearby vegetation is mostly moss and/or conifers. "},{"$f":"F!D101","v":0},null,null,{"$f":"1-D78","v":1},"Stain8","Stained waters usually have less aquatic productivity and lower biomass of aquatic invertebrates. "]
[{"$f":"F!A102","v":"F22"},{"$f":"F!B102","v":"Fish"},{"$f":"F!C102","v":"Fish (native or stocked) are known to be present in the AA.  Or fish can access at least part of the AA during one or more days annually.  If uncertain, use answer from Form OF, item  OF15, or enter \"0\"."},{"$f":"F!D102","v":0},null,null,{"$f":"1-D79","v":1},"Fish8","Fish can negatively impact the density and perhaps diversity of invertebrates in a stream or wetland (Hornung & Foote 2006). Disturbance of stream bottom sediments by spawning fish can temporarily change the composition and abundance of the stream invertebrate community in a localized area (Moore & Schindler 2008)."]
[{"$f":"F!A109","v":"F25"},{"$f":"F!B109","v":"Through Flow Pattern"},{"$f":"F!C109","v":"During its travel through the AA at the time of peak annual flow, most of the water arriving in channels [select only the ONE encountered by most of the incoming water]:"},null,null,null,{"$f":"IF((AllSat=1),\"\", IF((Inflows=0),\"\",MAX(F81:F85)/MAX(E81:E85)))","v":""},"ThruFlo8","Diffuse flow paths and large spatial complexity of channels within a wetland support a wider variety of microhabitats for invertebrates, so should result in greater species richness. In calculations, is excluded automatically (cell goes blank) if wetland never has surface water during an average year or if no surface inflows."]
[null,null,{"$f":"F!C110","v":"Does not bump into plant stems as it travels through the AA.  Nearly all the water continues to travel in unvegetated (often incised) channels that have little contact with wetland vegetation, or through a zone of open water such as an instream pond or lake."},{"$f":"F!D110","v":0},0,{"$f":"D81*E81","v":0}]
[null,null,{"$f":"F!C111","v":"bumps into herbaceous vegetation but mostly remains in fairly straight channels."},{"$f":"F!D111","v":0},1,{"$f":"D82*E82","v":0}]
[null,null,{"$f":"F!C112","v":"bumps into herbaceous vegetation and mostly spreads throughout, or is in widely  meandering, multi-branched, or braided channels."},{"$f":"F!D112","v":0},2,{"$f":"D83*E83","v":0}]
[null,null,{"$f":"F!C113","v":"bumps into tree trunks and/or shrub stems but mostly remains in fairly straight channels."},{"$f":"F!D113","v":0},1,{"$f":"D84*E84","v":0}]
[null,null,{"$f":"F!C114","v":"bumps into tree trunks and/or shrub stems and follows a fairly indirect path from entrance to exit (meandering, multi-branched, or braided)"},{"$f":"F!D114","v":0},2,{"$f":"D85*E85","v":0}]
[{"$f":"F!A125","v":"F28"},{"$f":"F!B125","v":"Groundwater: Strength of Evidence"},{"$f":"F!C125","v":"Select first applicable choice. "},null,null,null,{"$f":"IF((D89=1),\"\",MAX(F87:F89)/MAX(E87:E89))","v":0},"Groundw8","For invertebrates, groundwater provides a relatively steady input of nutrients that supports algal production. It also provides relatively warm temperatures and helps sustain low flows, thus increasing annual production of invertebrates (Brown et al. 2007).  However, where underlying geologic strata are iron-rich, groundwater discharge is accompanied by precipitation of iron \"floc\" in wetland sediment, smothering aquatic invertebrates and reducing their diversity. In calculations, is excluded automatically (cell goes blank) if no evidence of groundwater influx; otherwise is rated based on response in column D."]
[null,null,{"$f":"F!C126","v":"Groundwater monitoring has demonstrated that groundwater primarily discharges to the wetland for longer periods during the year than periods when the wetland recharges the groundwater.  Or, springs are known to be present within the AA.\n\n\n"},{"$f":"F!D126","v":0},3,{"$f":"D87*E87","v":0}]
[null,null,{"$f":"F!C127","v":"One or more of the following are true: (a) the upper end of the AA is located very close to the base of (but mostly not ON) a natural slope much steeper (usually >15%) than that within the AA and longer than 100 m, OR\n(b) rust deposits (\"iron floc\"), colored precipitates, or dispersible natural oil sheen are prevalent in the AA, OR\n(c) AA water is remarkably clear in contrast to naturally stained waters typical in nearby wetlands, OR\n(d) AA is located at a geologic fault.\n\n"},{"$f":"F!D127","v":0},2,{"$f":"D88*E88","v":0}]
[null,null,{"$f":"F!C128","v":"Neither of above is true, although some groundwater may discharge to or flow through the AA.  Or groundwater influx is unknown."},{"$f":"F!D128","v":0},0,{"$f":"D89*E89","v":0}]
[{"$f":"F!A140","v":"F31"},{"$f":"F!B140","v":"Interspersion of Herbaceous and Woody Cover"},{"$f":"F!C140","v":"The following best represents the distribution pattern of woody vegetation VS. unshaded herbaceous/ moss vegetation within the AA:"},null,null,null,{"$f":"MAX(F91:F94)/MAX(E91:E98)","v":0},"VegIntersp8","High interspersion of wetland woody and herbaceous vegetation provides emergence sites for aquatic insects and may be presumed to support more groups of wetland invertebrates."]
[null,null,{"$f":"F!C141","v":"(a) Woody cover and herbaceous/ moss cover EACH comprise 30-70% of the vegetated part of the AA, AND (b) There are many patches of woody vegetation scattered widely within herbaceous/ moss vegetation, or many patches of herbaceous vegetation scattered widely within woody vegetation."},{"$f":"F!D141","v":0},3,{"$f":"D91*E91","v":0},null,null,null,null,null," "]
[null,null,{"$f":"F!C142","v":"(a) Woody cover and herbaceous/ moss EACH comprise 30-70% of the vegetated AA, AND (b) There are few patches (\"islands\") of woody vegetation scattered widely within herbaceous vegetation, or few patches of herbaceous/ moss vegetation (\"gaps\") scattered widely within woody vegetation."},{"$f":"F!D142","v":0},2,0]
[null,null,{"$f":"F!C143","v":"(a) Woody cover OR herbaceous/ moss comprise >70% of the vegetated AA, AND (b) There are several patches of the other scattered within it. "},{"$f":"F!D143","v":0},1,0]
[null,null,{"$f":"F!C144","v":"(a) Woody cover OR herbaceous/ moss comprise >70% of the vegetated AA, AND (b) The other is absent or is mostly in a single area or distinct zone with almost no intermixing of woody and unshaded herbaceous/ moss vegetation."},{"$f":"F!D144","v":0},0,0]
[{"$f":"F!A160","v":"F34"},{"$f":"F!B160","v":"Downed Wood"},{"$f":"F!C160","v":"The number of downed wood pieces longer than 2 m and with diameter >10 cm, and not persistently submerged, is:"},null,null,null,{"$f":"IF((NoWoodyVeg=1),\"\",MAX(F96:F97))","v":0},"WoodDown8","Downed wood provides food, cover, and a stable microclimate for many  invertebrates that live in soil and peat of wetlands that seldom flood. In calculations, is excluded automatically (cell goes blank) if woody vegetation occupies <5% of the vegetated part of the AA."]
[null,null,{"$f":"F!C161","v":"Several ( >5 if AA is >5 hectares, less for smaller AAs)"},{"$f":"F!D161","v":0},1,{"$f":"D96*E96","v":0}]
[null,null,{"$f":"F!C162","v":"Few or none "},{"$f":"F!D162","v":0},0,{"$f":"D97*E97","v":0}]
[{"$f":"F!A172","v":"F37"},{"$f":"F!B172","v":"Broad-leaved Deciduous Trees and Shrubs"},{"$f":"F!C172","v":"The percentage of the AA's tree or shrub cover that is broad-leaved deciduous and is taller than 1 meter is:"},null,null,null,{"$f":"IF((NoWoodyVeg=1),\"\",MAX(F99:F103)/MAX(E99:E103))","v":0},"Hardwood8","On a per-surface-area basis, deciduous trees often support higher levels of insect biomass than conifers, at least among nocturnal flying insects (Ober and Hayes 2008). In calculations, is excluded automatically (cell goes blank) if no woody vegetation in the wetland."]
[null,null,{"$f":"F!C173","v":"<1%, or largest patch occupies less than 0.01 hectare"},{"$f":"F!D173","v":0},0,{"$f":"D99*E99","v":0}]
[null,null,{"$f":"F!C174","v":"1-25% of the tree or shrub cover (whichever has more)"},{"$f":"F!D174","v":0},1,{"$f":"D100*E100","v":0}]
[null,null,{"$f":"F!C175","v":"25-50% of the tree or shrub cover (whichever has more)"},{"$f":"F!D175","v":0},2,{"$f":"D101*E101","v":0}]
[null,null,{"$f":"F!C176","v":"50-75% of the tree or shrub cover (whichever has more)"},{"$f":"F!D176","v":0},3,{"$f":"D102*E102","v":0}]
[null,null,{"$f":"F!C177","v":">75% of the tree or shrub cover (whichever has more)"},{"$f":"F!D177","v":0},4,{"$f":"D103*E103","v":0}]
[{"$f":"F!A178","v":"F38"},{"$f":"F!B178","v":"N Fixers"},{"$f":"F!C178","v":"The percent of the AA's shrub plus ground cover that is nitrogen-fixing plants (e.g., alder, baltic (wire) rush, sweetgale, lupine, clover, other legumes) is:"},null,null,null,{"$f":"MAX(F105:F109)/MAX(E105:E109)","v":0},"Nfixers8","Leaves of nitrogen-fixing plants such as alder have been shown to support higher densities and richness of aquatic and terrestrial invertebrates (Wipfli et al. 2007, Wipfli & Musselwhite 2004)."]
[null,null,{"$f":"F!C179","v":"<1% or none"},{"$f":"F!D179","v":0},0,{"$f":"D105*E105","v":0}]
[null,null,{"$f":"F!C180","v":"1-25% of the shrub plus ground cover, in the AA or along its water edge (whichever has more)."},{"$f":"F!D180","v":0},1,{"$f":"D106*E106","v":0}]
[null,null,{"$f":"F!C181","v":"25-50% of the shrub plus ground cover, in the AA or along its water edge (whichever has more)."},{"$f":"F!D181","v":0},2,{"$f":"D107*E107","v":0}]
[null,null,{"$f":"F!C182","v":"50-75% of the shrub plus ground cover, in the AA or along its water edge (whichever has more)."},{"$f":"F!D182","v":0},3,{"$f":"D108*E108","v":0}]
[null,null,{"$f":"F!C183","v":">75% of the shrub plus ground cover, in the AA or along its water edge (whichever has more)."},{"$f":"F!D183","v":0},4,{"$f":"D109*E109","v":0}]
[{"$f":"F!A188","v":"F40"},{"$f":"F!B188","v":"Moss Extent"},{"$f":"F!C188","v":"Within the part of the AA that lacks persistent surface water, the cover of moss is:"},null,null,null,{"$f":"MAX(F111:F115)/MAX(E111:E115)","v":0},"Moss8","Extensive moss cover creates acidic conditions that can restrict the number of aquatic invertebrate species in a wetland.  Moss also provides less vertical structure than most vascular plants."]
[null,null,{"$f":"F!C189","v":"<5% of the ground cover"},{"$f":"F!D189","v":0},3,{"$f":"D111*E111","v":0}]
[null,null,{"$f":"F!C190","v":"5-25% of the ground cover"},{"$f":"F!D190","v":0},3,{"$f":"D112*E112","v":0}]
[null,null,{"$f":"F!C191","v":"25-50% of the ground cover"},{"$f":"F!D191","v":0},2,{"$f":"D113*E113","v":0}]
[null,null,{"$f":"F!C192","v":"50-95% of the ground cover"},{"$f":"F!D192","v":0},1,{"$f":"D114*E114","v":0}]
[null,null,{"$f":"F!C193","v":">95% of the ground cover"},{"$f":"F!D193","v":0},0,{"$f":"D115*E115","v":0}]
[{"$f":"F!A200","v":"F42"},{"$f":"F!B200","v":"Ground Irregularity"},{"$f":"F!C200","v":"Consider the parts of the AA that lack surface water at some time of the year.  Excluding slash from logging, the number of small pits, raised mounds, hummocks, boulders, upturned trees, animal burrows, gullies, natural levees, wide soil cracks, and microdepressions is:"},null,null,null,{"$f":"MAX(F117:F119)/MAX(E117:E119)","v":0},"Girreg8","Greater microtopography implies greater heterogeneity of water, vegetation, and disturbance regimes, which together should indicate higher capacity to support a wide variety of invertebrates."]
[null,null,{"$f":"F!C201","v":"Few or none (minimal microtopography; <1% of that area) "},{"$f":"F!D201","v":0},0,{"$f":"D117*E117","v":0}]
[null,null,{"$f":"F!C202","v":"Intermediate"},{"$f":"F!D202","v":0},1,{"$f":"D118*E118","v":0}]
[null,null,{"$f":"F!C203","v":"Several (extensive micro-topography)"},{"$f":"F!D203","v":0},2,{"$f":"D119*E119","v":0}]
[{"$f":"F!A235","v":"F49"},{"$f":"F!B235","v":"Dominance of Most Abundant Herbaceous Species "},{"$f":"F!C235","v":"Determine which two native herbaceous (forb and graminoid) species comprise the greatest portion of the herbaceous cover that is unshaded by a woody canopy.  Then choose one of the following:"},null,null,null,{"$f":"IF((NoHerbCov=1),\"\", MAX(F121:F122)/MAX(E121:E122))","v":0},"HerbDiv8","The second condition implies greater diversity of plants, which sometimes is associated with greater diversity of aquatic invertebrates.  In calculations, is excluded automatically (cell goes blank) if vegetation in the wetland is <5% herbaceous."]
[null,null,{"$f":"F!C236","v":"those species together comprise > 50% of the areal cover of native herbaceous plants at any time during the year."},{"$f":"F!D236","v":0},0,{"$f":"D121*E121","v":0}]
[null,null,{"$f":"F!C237","v":"those species together do not comprise > 50% of the areal cover of native herbaceous plants at any time during the year."},{"$f":"F!D237","v":0},1,{"$f":"D122*E122","v":0}]
[{"$f":"F!A249","v":"F52"},{"$f":"F!B249","v":"Natural Cover in Buffer"},{"$f":"F!C249","v":"Along the wetland-upland edge and extending 30 m upslope, the percentage of the upland that contains natural (not necessarily native -- see column E) land cover taller than 10 cm is:"},null,null,null,{"$f":"MAX(F124:F128)/MAX(E124:E128)","v":0},"BuffNatPct8","Comparing data from multiple regions, Utz et al. (2009) reported that once urbanization in a watershed reached 60%, all taxa remaining responded either neutrally or positively with respect to continued urbanization. Most were harmed at much lower levels. The importance of streamside vegetation, especially trees, for sustaining the health of aquatic systems has been documented in the Pacific Northwest (e.g., Gregory et al. 1991, Naiman et al. 2000, Richardson et al. 2005, Wipfli et al. 2007). The positive effect is partly because wood falling into streams increases channel complexity which benefits aquatic invertebrates and fish; that may not apply to wood falling into wetlands.  Trees also help maintain stream temperature and streams adjoined by natural vegetation support richer and healthier aquatic invertebrate communities (Richards et al. 1996). However, the effects of buffers and/or tree canopy closure on aquatic life in perennial streams vary, with some studies showing little effect on native fish (Roy et al. 2005, Fischer et al. 2010) and others a positive effect especially when buffer width was at least 100 ft (Frimpong et al. 2005, Horwitz et al. 2008). A 30-ft wide buffer along perennial streams in British Columbia was found to be insufficient to protect stream invertebrate communities from adverse effects of clear-cut logging, although the terrestrial insects the buffer provided were noted as a potentially important food source for fish using the streams (Hoover et al. 2007). Another study of BC perennial streams found uncut riparian buffers of at least 30 ft were needed to limit changes from clear-cut logging to aquatic life in headwater forested watersheds; those changes included increase abundance of aquatic invertebrates and algae (Kiffney et al. 2003). Increased sunlight from vegetation removal can increase stream and wetland productivity and thus the density of some invertebrate groups, where nutrients and elevation (stream temperature) are not severely limiting (Moldenke & Linden 2007)."]
[null,null,{"$f":"F!C250","v":"<5% "},{"$f":"F!D250","v":0},0,{"$f":"D124*E124","v":0}]
[null,null,{"$f":"F!C251","v":"5 to 30%"},{"$f":"F!D251","v":0},2,0]
[null,null,{"$f":"F!C252","v":"30 to 60%"},{"$f":"F!D252","v":0},3,0]
[null,null,{"$f":"F!C253","v":"60 to 90%"},{"$f":"F!D253","v":0},4,0]
[null,null,{"$f":"F!C254","v":">90%.  SKIP to F54 (Cliffs)."},{"$f":"F!D254","v":0},6,0]
[{"$f":"F!A255","v":"F53"},{"$f":"F!B255","v":"Type of Cover in Buffer"},{"$f":"F!C255","v":"Within 30 m upslope of the wetland-upland edge closest to the AA, the upland land cover that is NOT unmanaged vegetation or water is mostly (mark ONE):"},null,null,null,{"$f":"IF((BuffAllNat=1),\"\",MAX(F130:F131)/MAX(E130:E131))","v":0},"CUbuffLUtype8","In calculations, is excluded automatically (cell goes blank) if natural cover in the buffer (see above) is >90%."]
[null,null,{"$f":"F!C256","v":"impervious surface, e.g., paved road, parking lot, building, exposed rock."},{"$f":"F!D256","v":0},0,0]
[null,null,{"$f":"F!C257","v":"bare or nearly bare pervious surface or managed vegetation, e.g., lawn, annual crops, mostly-unvegetated clearcut, landslide, unpaved road, dike."},{"$f":"F!D257","v":0},1,0]
[{"$f":"F!A312","v":"F66"},{"$f":"F!B312","v":"Water Quality Problem Area Located Upslope"},{"$f":"F!C312","v":"Sampling indicates problems with the quality of surface waters or sediment within the AA, or within 5 km upstream or upslope, as caused by (enter 1 for ALL that apply):"},null,null,null,{"$f":"IF((D137=1), \"\", MAX(D134:D136))","v":0},"WQprob8","If water containing toxic substances enters the wetland, the wetland has much less capacity to support aquatic invertebrates, and assemblages of those will be less diverse."]
[null,null,{"$f":"F!C313","v":"nutrients (phosphorus, nitrate, ammonia), or a water body within 5 km that contributes to the AA has been labeled \"hyper-eutrophic\" based on excessive levels of either total phosphorus or chlorophyll-a."},{"$f":"F!D313","v":0}]
[null,null,{"$f":"F!C314","v":"suspended sediment or turbidity"},{"$f":"F!D314","v":0}]
[null,null,{"$f":"F!C315","v":"metals (mercury, lead, zinc, copper, cadmium, others)"},{"$f":"F!D315","v":0}]
[null,null,{"$f":"F!C316","v":"petrochemicals (pesticides, herbicides, PCBs, others)"},{"$f":"F!D316","v":0}]
[null,null,{"$f":"F!C317","v":"None of above, or no data. "},{"$f":"F!D317","v":0}]
[{"$f":"S!A3","v":"S5"},{"$f":"S!B3","v":"Altered Timing of Water Inputs"},{"$f":"S!E17","v":"Stressor Subscore="},{"$f":"S!C17","v":0},null,null,{"$f":"IF((AllSat+AllSat1>0),\"\", 1-(S!F17))","v":1},"AltTime8","Life histories of most invertebrates are closely linked to specific thermal and light (seasonality) conditions as those interact with specific hydrologic patterns. Abnormal patterns of inundation to which invertebrate communities are not adapted may reduce populations of many intolerant invertebrate species, thus diminishing local biodiversity. In calculations, is excluded automatically (cell goes blank) if wetland never has surface water during an average year."]
[{"$f":"S!A18","v":"S6"},{"$f":"S!B18","v":"Accelerated Inputs of Contaminants and/or Salts"},"Stressor Subscore=",{"$f":"S!F32","v":0},null,null,{"$f":"1-(S!F18)","v":1},"Toxic8","If water containing toxic substances enters the wetland, the wetland has much less capacity to support aquatic invertebrates, and assemblages of those will be less diverse."]
[{"$f":"S!A46","v":"S8"},{"$f":"S!B46","v":"Excessive Sediment Loading from Contributing Area"},{"$f":"S!E63","v":"Stressor Subscore="},{"$f":"(S!C63)","v":0},null,null,{"$f":"1-(S!F63)","v":1},"SedCA8","Aquatic invertebrate communities (both benthic and planktonic) are harmed by excessive sedimentation and turbidity from sediment runoff. Sediment from timber-harvest activity (clearings and roads) can intensify the turbidity effects of spawning-salmon disturbance on macroinvertebrates (Campbell et al. 2011). Following timber harvests, the deposition of fine sediment can limit populations of grazing invertebrates even when algal foods become more available (Kiffney & Bull 2000). "]
[{"$f":"S!A64","v":"S9"},{"$f":"S!B64","v":"Soil or Sediment Alteration Within the Assessment Area"},{"$f":"S!E81","v":"Stressor Subscore="},{"$f":"S!C81","v":0},null,null,{"$f":"1-(S!F81)","v":1},"SoilDisturb8","Many wetland invertebrates inhabit the soil, and potentially are harmed by soil disturbance such as from tillage or compaction."]
[null,null,null,null,null,null,null," "]
[null,null,"Hydrologic Environment [WaterI]"]
[null,null,"AVERAGE(WatProb, Spring, Girreg8, Groundw8, SatPct8, PermWpct8, SeasPct8)",null,null,null,{"$f":"IFERROR(AVERAGE(WatProb, Spring, Girreg8, Groundw8, SatPct8, PermWpct8, SeasPct8),\"\")","v":0}]
[]
[null,null,"Aquatic Habitat Structure [HabStrucI]"]
[null,"Wetlands <10 hectares:","AVERAGE(ClassRichIn8, WetPerim2Area, WetVegArea, OWpct8, HerbDiv8, ThruFlo8, WoodDown8,  Interspers8, VegIntersp8, DepthDiv8, AqCov8)  ",null,null,null,{"$f":"IF((GT10HA=1),G148, IFERROR(AVERAGE(ClassRichIn, WetPerim2Area, WetVegArea, OWpct8, HerbDiv8, ThruFlo8, WoodDown8,  Interspers8, VegIntersp8, DepthDiv8, AqCov8),\"\"))","v":0}]
[null,"Wetlands >10 hectares:","Substituted ClassRichIn, OWpct, MixWaterVeg, MixHerbWood",null,null,null,{"$f":"IFERROR(AVERAGE(ClassRichIn, WetPerim2Area, WetVegArea, OWpct_INV, HerbDiv8, ThruFlo8, WoodDown8, MixWaterVeg, MixHerbWood, DepthDiv8, AqCov8),\"\")","v":0}]
[]
[null,null,"Primary Productivity [CfixI]"]
[null,null,"AVERAGE(GrowDD, Moss8, Stain8, Hardwood8, Depth8, Fluc8, Nfixers8)",null,null,null,{"$f":"IFERROR(AVERAGE(GrowDD, Moss8, Stain8, Hardwood8, Depth8, Fluctu8, Nfixers8 ),\"\")","v":0.16666666666666666}]
[]
[null,null,"Stressors (or lack of)  [Stress I]"]
[null,null,"AVERAGE(SedCA8, Toxic8, AltTime8, SoilDisturb8, BuffNatPct8, NatCov1k, Fish8, PerimNatCov, WQprob8, WQrisk)",null,null,null,{"$f":"IFERROR(AVERAGE(SedCA8, Toxic8, AltTime8, Fish8,SoilDisturb8, BuffNatPct8, NatCov1k, PerimNatCov, WQprob8, WQrisk),\"\")","v":0.7142857142857143}]
[]
[null,null,"ABWRET-A FUNCTION MODEL"]
[null,null,"Aquatic Invertebrate Habitat"]
[null,null,"AVERAGE(MarshPct, MarshUniq, AVERAGE(WaterI, HabStrucI, CfixI, StressI))",null,null,null,{"$f":"10*AVERAGE(MarshPct, MarshUniq, AVERAGE(WaterI1a, HabStrucI1a,  CfixI1a, StressI1a))","v":2.2023809523809526}]
[null,null,null,null,null,null,null,null,"Literature Cited"]
[null,null,"ABWRET-E model:",null,null,null,null,null,"Alsfeld, A. J., J. L. Bowman, and A. Deller-Jacobs. 2009. Effects of woody debris, microtopography, and organic matter amendments on the biotic community of constructed depressional wetlands. Biological Conservation 142:247-255."]
[null,1,"Calculate these averages:",null,null,null,null,null,"Baxter, C. V., K. D. Fausch, and W. Carl Saunders. 2005. Tangled webs: reciprocal flows of invertebrate prey link streams and riparian zones. Freshwater Biology 50:201-220."]
[null,"a","AVERAGE(MixWaterVeg, OWpct) ",{"$f":"IFERROR(AVERAGE(MixWaterVeg, OWpct_INV),\"\")","v":""},null,null,null,null,"Brown, J. 2007. Groundwater and Biodiversity Conservation.  in: A. Wyers, A. Aldous, and L. Bach, editors. A Methods Guide for Integrating Groundwater Needs of Ecosystems and Species into Conservation Plans in the Pacific Northwest. The Nature Conservancy, Portland, OR."]
[null,"b","AVERAGE (MixHerbWood, ClassRichIn) ",{"$f":"IFERROR(AVERAGE(MixHerbWood, ClassRichIn),\"\")","v":""},null,null,null,null,"Bunn, S. and A. Arthington. 2002. Basic principles and ecological consequences of altered flow regimes for aquatic biodiversity. Environmental Management 30:492–507."]
[null,"c","AVERAGE(ClassRich1k, WetDens1k_NoBog)",{"$f":"IFERROR(AVERAGE(ClassRich1k, WetDens1k_NoBog),\"\")","v":""},null,null,null,null,"Campbell, E. Y., M. E. Benbow, S. D. Tiegs, J. P. Hudson, G. A. Lamberti, and R. W. Merritt. 2011. Timber harvest intensifies spawning-salmon disturbance of macroinvertebrates in southeastern Alaskan streams. Journal of the North American Benthological Society 30:49-59."]
[null,"d","AVERAGE(Dist2DevCrop, NatCov1k, PerimNatCov)",{"$f":"IFERROR(AVERAGE(Dist2DevCrop, NatCov1k, PerimNatCov),\"\")","v":""},null,null,null,null,"Cannings, S. G. and R. A. Cannings. 1994. The Odonata of the northern Cordilleran peatlands of North America. Memoirs of the Entomological Society of Canada 169:89-110."]
[null,2,"10*AVERAGE (MarshPct, UniqClass, a, b, c, d)",{"$f":"IFERROR(10*AVERAGE(MarshPct, UniqClass,D162:D165),\"\")","v":""},null,null,null,null,"Corcoran, R. M., J. R. Lovvorn, and P. J. Heglund. 2009. Long-term change in limnology and invertebrates in Alaskan boreal wetlands. Hydrobiologia 620:77–89."]
[null,null,null,null,null,null,null,null,"Fischer, J. R., M. C. Quist, S. L. Wigen, A. J. Schaefer, T. W. Stewart, and T. M. Isenhart. 2010. Assemblage and population-level responses of stream fish to riparian buffers at multiple spatial scales. Transactions of the American Fisheries Society 139:185-200."]
[null,null,"ABWRET-E with substitutions:",null,null,null,null,null,"Frimpong, E. A., T. M. Sutton, K. J. Lim, P. J. Hrodey, B. A. Engel, T. P. Simon, J. G. Lee, and D. C. LeMaster. 2005. Determination of optimal riparian forest buffer dimensions for stream biota-landscape association models using multi metric and multi variate responses. Canadian Journal of Fisheries and Aquatic Sciences 62:1-6."]
[null,1,"Calculate these averages:",null,null,null,null,null,"Gregory, S. V., F. J. Swanson, W. A. McKee, and K. W. Cummins. 1991. An ecosystem perspective of riparian zones: Focus on links between land and water. Bioscience 41:540-550."]
[null,"a","AVERAGE(Interspers8, OWpct8) ",{"$f":"IFERROR(AVERAGE(Interspers8, OWpct8),\"\")","v":0},null,null,null,null,"Hernandez, O., R. W. Merritt, and M. S. Wipfli. 2005. Benthic invertebrate community structure is influenced by forest succession after clearcut logging in southeastern Alaska. Hydrobiologia 533:45-59."]
[null,"b","AVERAGE (VegIntersp8, ClassRichIn) ",{"$f":"IFERROR(AVERAGE(VegIntersp8,ClassRichIn),\"\")","v":0},null,null,null,null,"Holmquist, J., J. Jones, J. Schmidt-Gengenbach, L. Pierotti, and J. Love. 2011. Terrestrial and Aquatic Macroinvertebrate Assemblages as a Function of Wetland Type across a Mountain Landscape. Institute of Arctic and Alpine Research, University of Colorado, Boulder, CO."]
[null,"c","AVERAGE(ClassRich1k, WetDens1k_NoBog)",{"$f":"IFERROR(AVERAGE(ClassRich1k, WetDens1k_NoBog),\"\")","v":""},null,null,null,null,"Hoover, S. E. R., L. G. W. Shannon, and J. D. Ackerman. 2007. The effect of riparian condition on invertebrate drift in mountain streams. Aquatic Sciences 69:544-553."]
[null,"d","AVERAGE(DistDevCrop, NatCov1k, PerimNatCov)",{"$f":"IFERROR(AVERAGE(Dist2DevCrop, NatCov1k, PerimNatCov),\"\")","v":""},null,null,null,null,"Hornung, J. and A. L. Foote. 2006. Aquatic invertebrate responses to fish presence and vegetation complexity in western boreal wetlands, with implications for Waterbird productivity. Wetlands 26:1-12."]
[null,2,"10*AVERAGE (MarshPct, UniqClass, a, b, c, d)",{"$f":"10*AVERAGE(MarshPct, UniqClass,D170:D173)","v":0},null,null,null,null,"Horwitz, R. J., T. E. Johnson, P. F. Overbeck, T. K. O'Donnell, W. C. Hession, and B. W. Sweeney. 2008. Effects of riparian vegetation and watershed urbanization on fishes in streams of the mid-Atlantic Piedmont (USA). Journal of the American Water Resources Association 44:724-741."]
[null,null,null,null,null,null,null,null,"Kiffney, P. M. and J. P. Bull. 2000. Factors controlling periphyton accrual during summer in headwater streams of southwestern British Columbia, Canada. Journal of Freshwater Ecology 15:339-351."]
[null,null,null,null,null,null,null,null,"Kiffney, P. M., J. S. Richardson, and J. P. Bull. 2003. Responses of periphyton and insects to experimental manipulation of riparian buffer width along forest streams. Journal of Applied Ecology 40:1060-1076."]
[null,null,null,null,null,null,null,null,"May, C. 2003. Stream-Riparian Ecosystems In the Puget Sound Lowland Eco-Region. A Review of Best Available Science. Watershed Ecology, LLC."]
[null,null,null,null,null,null,null,null,"McDade, M. H., F. J. Swanson, W. A. McKee, J. F. Franklin, and J. Van Sickle. 1990. Source  distances for coarse woody debris entering small streams in western Oregon and Washington USA. Canadian Journal of Forest Research 20:326-330."]
[null,null,null,null,null,null,null,null,"Meleason, M. A., S. V. Gregory, and J. P. Bolte. 2003. Implications of riparian management strategies on wood in streams of the Pacific Northwest. Ecological Applications 13:1212-1221."]
[null,null,null,null,null,null,null,null,"Moldenke, A. R. and C. V. Linden. 2007. Effects of clearcutting and riparian buffers on the yield of adult aquatic macroinvertebrates from headwater streams. Forest Science 53:308-319."]
[null,null,null,null,null,null,null,null,"Moore, J. W. and D. E. Schindler. 2008. Biotic disturbance and benthic community dynamics in salmon-bearing streams. Journal of Animal Ecology 77:275-284."]
[null,null,null,null,null,null,null,null,"Murphy, M. 1995. Forestry Impacts on Freshwater Habitat of Anadromous Salmonids in the Pacific Northwest and Alaska – Requirements for Protection and Restoration. NOAA Coastal Ocean Program Decision Analysis Series No. 7. U.S. Department of Commerce, National Oceanic and Atmospheric Administration Coastal Ocean Office, NOAA Coastal Ocean Office, Silver Springs, MD."]
[null,null,null,null,null,null,null,null,"Naiman, R. J., R. E. Bilby, and P. A. Bisson. 2000. Riparian ecology and management in the Pacific Coastal Rain Forest. Bioscience 50:996-1011."]
[null,null,null,null,null,null,null,null,"Nicholson, B. J. 1995. The wetlands of Elk Island National Park: Vegetation classification, water chemistry, and hydrotopographic relationships. Wetlands 15:119-133."]
[null,null,null,null,null,null,null,null,"Ober, H. K. and J. P. Hayes. 2008. Influence of forest riparian vegetation on abundance and biomass of nocturnal flying insects. Forest Ecology and Management 256:1124-1132."]
[null,null,null,null,null,null,null,null,"Richards, C., L. B. Johnson, and G. E. Host. 1996. Landscape-scale influences on stream habitats and biota. Canadian Journal of Fisheries and Aquatic Sciences 53:295-311."]
[null,null,null,null,null,null,null,null,"Richardson, J. S., R. E. Bilby, and C. A. Bondar. 2005. Organic matter dynamics in small streams of the Pacific Northwest. Journal of the American Water Resources Association 41:921-934."]
[null,null,null,null,null,null,null,null,"Robison, E. G. and R. L. Beschta. 1990. Identifying trees in riparian areas that can provide coarse woody debris to streams. Forest Science 36:790-801."]
[null,null,null,null,null,null,null,null,"Roth, B. M., I. C. Kaplan, G. G. Sass, P. T. Johnson, A. E. Marburg, A. C. Yannarell, T. D. Havlicek, T. V. Willis, M. G. Turner, and S. R. Carpenter. 2007. Linking terrestrial and aquatic ecosystems: The role of woody habitat in lake food webs. Ecological Modelling 203:439-452."]
[null,null,null,null,null,null,null,null,"Roy, A. H., C. L. Faust, M. C. Freeman, and J. L. Meyer. 2005. Reach-scale effects of riparian forest cover on urban stream ecosystems. Canadian Journal of Fisheries and Aquatic Sciences 62:2312-2329."]
[null,null,null,null,null,null,null,null,"Utz, R. M., R. H. Hilderbrand, and D. M. Boward. 2009. Identifying regional differences in threshold responses of aquatic invertebrates to land cover gradients. Ecological Indicators 9:556-567."]
[null,null,null,null,null,null,null,null,"Sickle, J. V. and S. V. Gregory. 1990. Modeling inputs of large woody debris to streams from falling trees. Canadian Journal of Forest Research 20:1593-1601."]
[null,null,null,null,null,null,null,null,"Waite, I. R., S. Sobieszczyk, K. D. Carpenter, A. J. Arnsberg, H. M. Johnson, C. A. Hughes, M. J. Sarantou, and F. A. Rinella. 2008. Effects of Urbanization on Stream Eco-Systems in the Willamette River Basin and Surrounding Area,Oregon and Washington: U.S. Geological Survey Scientific Investigations Report 2006–5101–D., U.S. Geological Survey, Portland, OR."]
[null,null,null,null,null,null,null,null,"Wenger, S. and L. Fowler. 2000. Protecting stream and river corridors : creating effective local riparian buffer ordinances. Carl Vinson Institute of Government, the University of Georgia, Athens, GA."]
[null,null,null,null,null,null,null,null,"Wipfli, M. S. and J. Musslewhite. 2004. Density of red alder (Alnus rubra) in headwaters influences invertebrate and detritus subsidies to downstream fish habitats in Alaska. Hydrobiologia 520:153-163."]
[null,null,null,null,null,null,null,null,"Wipfli, M. S., J. S. Richardson, and R. J. Naiman. 2007. Ecological linkages between headwaters and downstream ecosystems: transport of organic matter, invertebrates, and wood down headwater channels. Journal of the American Water Resources Association 43:72-85."]

{"sheet":"AM","index":18,"n_rows":172,"n_cols":13,"rows_kept":172,"cut":false,"hidden":false,"merged":[[130,0,131,0],[119,0,123,0],[119,1,123,1],[124,8,129,8],[124,1,129,1],[124,0,129,0],[113,8,117,8],[113,1,117,1],[119,8,123,8],[119,7,123,7],[124,7,129,7],[113,7,117,7],[93,8,95,8],[96,0,99,0],[96,1,99,1],[96,8,99,8],[113,0,117,0],[106,8,112,8],[100,8,105,8],[100,7,105,7],[106,0,112,0],[106,1,112,1],[106,7,112,7],[96,7,99,7],[93,7,95,7],[100,0,105,0],[100,1,105,1],[93,0,95,0],[84,0,92,0],[65,0,69,0],[49,0,54,0],[70,0,73,0],[74,1,78,1],[74,0,78,0],[55,0,58,0],[70,1,73,1],[49,1,54,1],[65,8,69,8],[22,0,28,0],[79,7,83,7],[84,7,92,7],[74,7,78,7],[70,7,73,7],[65,7,69,7],[59,7,62,7],[42,7,48,7],[34,7,41,7],[55,7,58,7],[42,8,48,8],[22,8,28,8],[84,1,92,1],[59,1,62,1],[65,1,69,1],[49,7,54,7],[29,7,33,7],[22,7,28,7],[79,0,83,0],[34,0,41,0],[42,1,48,1],[59,0,62,0],[22,1,28,1],[55,1,58,1],[79,1,83,1],[42,0,48,0],[29,0,33,0],[29,1,33,1],[79,8,83,8],[59,8,62,8],[0,4,0,8],[130,1,131,1],[130,7,131,7],[130,8,131,8],[0,0,0,1],[49,8,54,8],[55,8,58,8],[29,8,33,8],[93,1,95,1],[70,8,73,8],[74,8,78,8],[34,1,41,1],[34,8,41,8],[84,8,92,8]]}
["Amphibian             Habitat",null,"The capacity to support or contribute to an abundance or diversity of native frogs, toads, and salamanders.","AM"]
["#","Function Indicators from Estimator","Scoring Notes",null,null,null,"Normalised Score","Indicator Abbreviation or Formula","Rationale"]
[{"$f":"OF!A6","v":"OF5"},{"$f":"OF!C6","v":"Wetland Class Richness Within 1km"},null,null,null,null,{"$f":"IF((ClassRich1k=\"\"),\"\",ClassRich1k)","v":""},"ClassRich1k","To some degree, different wetland classes satisfy different requirements of amphibians during their life cycle.  Thus, greater class richness may support greater amphibian productivity and/or diversity.  A 1-km buffer as well as on-site condition is assessed because many amphibians conduct essential dispersal movements over distances that long or longer."]
[{"$f":"OF!A7","v":"OF6"},{"$f":"OF!C7","v":"Wetland Class Richness Within Wetland"},null,null,null,null,{"$f":"IF((ClassRichIn=\"\"),\"\",ClassRichIn)","v":""},"ClassRichIn","See above."]
[{"$f":"OF!A8","v":"OF7"},{"$f":"OF!C8","v":"Distance to Nearest Annual Cropland or Developed Land"},null,null,null,null,{"$f":"IF((Dist2DevCrop=\"\"),\"\",Dist2DevCrop)","v":""},"Dist2DevCrop","Wetlands located near agricultural and developed areas are often exposed to greater amounts of pesticides and other contaminants.  Those can reduce amphibian productivity by contributing to deformities as well as increased vulnerability to fungal infections and parasites."]
[{"$f":"OF!A9","v":"OF8"},{"$f":"OF!C9","v":"Distance to Nearest Road (from Wetland Edge)"}," ",null,null,null,{"$f":"IF((Dist2Road=\"\"),\"\",Dist2Road)","v":""},"Dist2Road","Roads and/or traffic are a significant barrier to dispersing amphibians (Mader 1984, Fahrig et al. 1995, and see review by Fahrig & Rytwinski 2009).  In Ontario (Eigenbrod 2008a) and Virginia (Marsh 2007), “accessible habitat” -- defined as the habitat available to pond-dwelling amphibians without individuals needing to cross a major road -- was a better predictor of amphibian species richness than simply the amount of habitat within some distance of breeding ponds (Eigenbrod 2008b).  Narrow roads gated to exclude traffic were crossed more often than roads with traffic by terrestrial salamanders in Virginia (Marsh 2007).  Remarkably, even some narrow logging roads that had long been abandoned continued to impair movements and densities of salamanders in North Carolina; the road effect appeared to extend about 115 ft into the adjoining woods on both sides of the road (Semlitsch et al. 2007). "]
[{"$f":"OF!A16","v":"OF15"},{"$f":"OF!C16","v":"Fish Presence"},"Inverse",null,null,null,{"$f":"IF((FishPres=\"\"),\"\",1-FishPres)","v":""},"FishPres","Populations of some amphibians (e.g., four-toed salamander) seem to thrive best in fishless wetlands. Predatory fish (especially, exotic species) can cause extirpations of native species or at least reduce productivity (Pearl et al. 2005)."]
[{"$f":"OF!A18","v":"OF17"},{"$f":"OF!C18","v":"Growing Degree Days"}," ",null,null,null,{"$f":"IF((GrowDD=\"\"),\"\",GrowDD)","v":""},"GrowDD","Amphibians do not physiologically regulate their body temperature.  Thus in boreal regions their populations are likely to be more productive (and have greater survival) in warmer parts of the region."]
[{"$f":"OF!A24","v":"OF23"},{"$f":"OF!C24","v":"% of the AA that is Marsh"},null,null,null,null,{"$f":"IF((MarshPct=\"\"),\"\",MarshPct)","v":""},"MarshPct","For many amphibians (e.g., northern leopard frog), wetlands classified as marsh provide the best habitat."]
[{"$f":"OF!A28","v":"OF27"},{"$f":"OF!C28","v":"Interspersion Index for Internal Water & Vegetation (macroscale)"}," ",null,null,null,{"$f":"IF((MixWaterVeg=\"\"),\"\",MixWaterVeg)","v":""},"MixWaterVeg","Wetlands with a nearly even mix of well-interspersed vegetative cover and open water tend to be more supportive of amphibians because such conditions provide both egg attachment sites and productive open-water foraging areas for tadpoles."]
[{"$f":"OF!A29","v":"OF28"},{"$f":"OF!C29","v":"% Natural Cover within 1km"}," ",null,null,null,{"$f":"IF((NatCov1k=\"\"),\"\",NatCov1k)","v":""},"NatCov1k","Amphibians require upland habitat as well as aquatic habitat. Uplands that are dominated by natural vegetation usually provide the most suitable microclimates and habitat structure. Unvegetated or artificially vegetated surfaces can inhibit movements of some species to those  upland habitats. The type of non-natural land cover that surrounds a wetland can influence dispersal success of amphibians.  Unvegetated lands are usually the least suitable.  Clearcuts may be better but perhaps still not as suitable as natural cover on soils of similar productivity. Larger contiguous tracts of nearby natural land are more likely to meet the habitat needs of dispersing amphibians than small or fragmented patches."]
[{"$f":"OF!A33","v":"OF32"},{"$f":"OF!C33","v":"% of AA that is Open Water (macro scale, Amphibian Habitat)"},"The raw value is scored as follows: <1%=0.2;  1%-99%=1.0; >99%=0.",null,null,null,{"$f":"IF((OWpct_AM=\"\"),\"\",OWpct_AM)","v":""},"OWpct_AM","Unshaded open water areas provide warmer conditions favored by many amphibians and generally support higher primary productivity.  However, at least a little wetland vegetation must be present to provide cover from predatory fish and for egg attachment sites.  "]
[{"$f":"OF!A35","v":"OF34"},{"$f":"OF!C35","v":"% of Wetland Perimeter Adjoined by Natural Cover"}," ",null,null,null,{"$f":"IF((PerimNatCov=\"\"),\"\",PerimNatCov)","v":""},"PerimNatCov","See OF28 above."]
[{"$f":"OF!A41","v":"OF40"},{"$f":"OF!C41","v":"Road Density in 1km Buffer"},"Inverse",null,null,null,{"$f":"IF((RdDens1k=\"\"),\"\",RdDens1k)","v":""},"RdDens1k","See OF 8 above."]
[{"$f":"OF!A45","v":"OF44"},{"$f":"OF!C45","v":"Within Range of a Sensitive Amphibian"},"If not within sensitive amphibian range then cell turns blank (NULL) and is ignored in calculations.",null,null,null,{"$f":"IF((SensAm=\"\"),\"\",IF((SensAm=1),1,\"\"))","v":""},"SensAm","Because of their relative rarity, these amphibian species contribute more to regional biodiversity than amphibian species with broader habitat tolerances."]
[{"$f":"OF!A51","v":"OF50"},{"$f":"OF!C51","v":"Springs within 300m"},"If wetland lacks a spring then this indicator is ignored (NULL) in calculations.",null,null,null,{"$f":"IF((Spring=\"\"),\"\",IF((Spring=1),1,\"\"))","v":""},"Spring","Especially in dry regions, springs provide relatively stable and predictable habitat for some amphibian species."]
[{"$f":"OF!A59","v":"OF58"},{"$f":"OF!C59","v":"FenSwampMarshPct/ FenSwampMarshPct1k"}," ",null,null,null,{"$f":"IF((UniqFenMarshSwamp=\"\"),\"\",UniqFenMarshSwamp)","v":""},"UniqFenMarsh Swamp","If a wetland contains fen, marsh, or swamp but those classes (which are most important to amphibians) are scarce in the surrounding area, the contribution of amphibian species (that associate with those classes) to local biodiversity is likely to be greater."]
[{"$f":"OF!A64","v":"OF63"},{"$f":"OF!C64","v":"Wetland Density Within 1km"},null,null,null,null,{"$f":"IF((WetDens1k=\"\"),\"\",WetDens1k)","v":""},"WetDens1k","Frogs, snakes, and aquatic salamanders frequently use multiple wetlands in close proximity, such that wetlands located within landscapes with a high proportion of wetland cover are more likely to cumulatively meet the needs of these species, especially for dispersal to alternative breeding sites during years of drought. One amphibian study found that the amount of available habitat within a given radius of a patch was more successful at predicting successful amphibian immigration than distance to nearest patch of suitable habitat (Bender 2003). "]
[{"$f":"OF!A65","v":"OF64"},{"$f":"OF!C65","v":"Wetland Density Within 1km (excluding bogs)"}," ",null,null,null,{"$f":"IF((WetDens1k_NoBog=\"\"),\"\",WetDens1k_NoBog)","v":""},"WetDens1k_NoBog","See above.  Bogs are excluded because of their generally lower use by most amphibian species."]
[{"$f":"OF!A71","v":"OF70"},{"$f":"OF!C71","v":"Wind Energy - Summer"},"Inverse",null,null,null,{"$f":"IF((WindSumm=\"\"),\"\",1-WindSumm)","v":""},"WindSumm","The shelter and moist microclimate provided by wetland vegetation is especially critical to amphibians in areas with strong summer winds that tend to dry out the moist skin surfaces that are characteristic of amphibians."]
[{"$f":"OF!A73","v":"OF72"},{"$f":"OF!C73","v":"Surface Water Quality Risk Index"},"Inverse",null,null,null,{"$f":"IF((WQrisk=\"\"),\"\",1-WQrisk)","v":""},"WQrisk","Excessive suspended sediment can interfere with the respiration and reproduction of larval amphibians (Knutson et al. 2004). High levels of some substances from livestock use or wastewater effluent can harm amphibian populations and reduce amphibian diversity, e.g., Schmutzer et al. 2008)."]
["#","Function Indicators from Onsite Visit","Categorical Choices","Data","Weight","Data  x  Weight","Normalised Score","Indicator Abbreviation or Formula","Rationale & Scoring Notes"]
[{"$f":"F!A17","v":"F3"},{"$f":"F!B17","v":"% Saturated Only"},{"$f":"F!C17","v":"The percentage of the AA that never contains surface water during an average year (that is, except perhaps for a few hours after snowmelt or rainstorms), but which is still a wetland, is:"},null,null,null,{"$f":"MAX(F24:F29)/MAX(E24:E29)","v":0},"SatPct11","Wetlands that lack surface water throughout the year may still provide dispersal sites for adult frogs, toads, and salamanders, but do not provide reproductive habitat for most amphibian species."]
[null,null,{"$f":"F!C18","v":"less than 1%, or <0.01 hectare (about 10 m on a side) never has surface water.  In other words, all or nearly all of the AA is inundated permanently or at least seasonally."},{"$f":"F!D18","v":0},5,{"$f":"D24*E24","v":0}]
[null,null,{"$f":"F!C19","v":"1-25% of the AA never contains surface water."},{"$f":"F!D19","v":0},6,0]
[null,null,{"$f":"F!C20","v":"25-50% of the AA never contains surface water."},{"$f":"F!D20","v":0},4,0]
[null,null,{"$f":"F!C21","v":"50-99% of the AA never contains surface water."},{"$f":"F!D21","v":0},3,0]
[null,null,{"$f":"F!C22","v":">99% of the AA never contains surface water, except for water flowing in channels and/or in pools that occupy <1% of the AA. SKIP to F26 (Channel Connection & Outflow Duration)"},{"$f":"F!D22","v":0},2,0]
[null,null,{"$f":"F!C23","v":">99% of the AA never contains surface water, and AA is not intersected by channels that have flow, not even for a few days per year. SKIP to F26."},{"$f":"F!D23","v":0},1,0]
[{"$f":"F!A45","v":"F9"},{"$f":"F!B45","v":"Annual Water Fluctuation Range"},{"$f":"F!C45","v":"The annual fluctuation in surface water level within most of the parts of the AA that contain surface water is:"},null,null,null,{"$f":"IF((AllSat+AllSat>0),\"\",IF((NoSeasonal=1),\"\",MAX(F31:F34)/MAX(E31:E34)))","v":0},"Fluctu11","Egg masses of many frogs and aquatic salamanders are more susceptible to stranding in wetlands with large water level fluctuations. In calculations, is excluded automatically (cell goes blank) if wetland never has surface water during an average year, or if none of it floods only seasonally."]
[null,null,{"$f":"F!C46","v":"<10 cm change (stable) "},{"$f":"F!D46","v":0},5,{"$f":"D31*E31","v":0}]
[null,null,{"$f":"F!C47","v":"10 cm - 50 cm change"},{"$f":"F!D47","v":0},4,{"$f":"D32*E32","v":0}]
[null,null,{"$f":"F!C49","v":"1-2 m change"},{"$f":"F!D49","v":0},3,{"$f":"D33*E33","v":0}]
[null,null,{"$f":"F!C50","v":">2 m change"},{"$f":"F!D50","v":0},1,{"$f":"D34*E34","v":0}]
[{"$f":"F!A62","v":"F12"},{"$f":"F!B62","v":"% of Water Ponded vs. Flowing "},{"$f":"F!C62","v":"The percentage of the AA's surface water that is ponded (stagnant, or flows so slowly that fine sediment is not held in suspension) during most of the time it is present, and which is either open or shaded by emergent vegetation is:"},null,null,null,{"$f":"IF((AllSat+AllSat>0),\"\", IF((SmallAA=1),\"\", MAX(F36:F42)/MAX(E36:E42)))","v":0},"IsoWet11","Pools that remain isolated from other surface waters even during high water provide amphibians with the most protection from predatory fish.  More amphibian species prefer ponded water than water flowing in channels. In calculations, is excluded automatically (cell goes blank) if wetland never has surface water during an average year or is <0.01 ha."]
[null,null,{"$f":"F!C63","v":"<1% or none, or occupies <0.01 hectare cumulatively.  Nearly all water is flowing.  Enter \"1\" and SKIP to F21 (Stained Surface Water)."},{"$f":"F!D63","v":0},0,{"$f":"D36*E36","v":0}]
[null,null,{"$f":"F!C64","v":"1-5% of the water, and mainly in small pools.  The rest is flowing."},{"$f":"F!D64","v":0},2,0]
[null,null,{"$f":"F!C65","v":"1-5% of the water, and mainly in a single large pool or pond.  The rest is flowing."},{"$f":"F!D65","v":0},1,0]
[null,null,{"$f":"F!C66","v":"5-30% of the water"},{"$f":"F!D66","v":0},3,0]
[null,null,{"$f":"F!C67","v":"30-70% of the water"},{"$f":"F!D67","v":0},4,0]
[null,null,{"$f":"F!C68","v":"70-95% of the water"},{"$f":"F!D68","v":0},5,0]
[null,null,{"$f":"F!C69","v":">95% of the water.  Little or no visibly flowing water within the AA."},{"$f":"F!D69","v":0},6,0]
[{"$f":"F!A71","v":"F14"},{"$f":"F!B71","v":"% of Ponded Water That Is Open "},{"$f":"F!C71","v":"In ducks-eye aerial view, the percentage of the ponded water that is open (lacking emergent vegetation during most of the growing season, and unhidden by a forest or shrub canopy) is:"},null,null,null,{"$f":"IF((AllSat+AllSat>0),\"\",IF((NoPonded=1),\"\", IF((SmallAA=1),\"\", MAX(F44:F49)/MAX(E44:E49))))","v":0},"OWpct11","The eggs and larvae of many frogs and aquatic salamanders can easily be harmed by excessive ultraviolet radiation.  Aquatic plants may provide some degree of shelter from such radiation, as well as providing attachment surfaces for eggs. In calculations, is excluded automatically (cell goes blank) if wetland never has surface water during an average year.  Also is excluded automatically if wetland has no ponded water or is <0.01 ha"]
[null,null,{"$f":"F!C72","v":"<1% or none, or largest pool occupies <0.01 hectares.  Enter \"1\" and SKIP to F20 (Floating Algae & Duckweed)."},{"$f":"F!D72","v":0},5,{"$f":"D44*E44","v":0}]
[null,null,{"$f":"F!C73","v":"1-5% of the ponded water.  Enter \"1\" and SKIP to F20."},{"$f":"F!D73","v":0},4,0]
[null,null,{"$f":"F!C74","v":"5-30% of the ponded water."},{"$f":"F!D74","v":0},3,0]
[null,null,{"$f":"F!C75","v":"30-70% of the ponded water."},{"$f":"F!D75","v":0},2,0]
[null,null,{"$f":"F!C76","v":"70-99% of the ponded water."},{"$f":"F!D76","v":0},1,0]
[null,null,{"$f":"F!C77","v":"100% of the ponded water. "},{"$f":"F!D77","v":0},0,0]
[{"$f":"F!A84","v":"F16"},{"$f":"F!B84","v":"Predominant Width of Vegetated Zone within Wetland"},{"$f":"F!C84","v":"At the driest time of year (or lowest water level), the average width of vegetated area in the AA that separates adjoining uplands from open water within the AA is:"},null,null,null,{"$f":"IF((AllSat+AllSat>0),\"\", IF((OpenW=0),\"\", IF((SmallAA=1),\"\", MAX(F51:F55)/MAX(E51:E55))))","v":""},"Vwidth11","Wider bands of wetland vegetation help protect a wetland's open waters from contaminants carried in from adjoining uplands. Wider bands of wetland vegetation also provide better cover for young frogs and salamanders as they transition to upland nonbreeding areas. In calculations, is excluded automatically (cell goes blank) if wetland never has surface water during an average year or if wetland lacks open water or is <0.01 ha."]
[null,null,{"$f":"F!C85","v":"<1 m"},{"$f":"F!D85","v":0},0,{"$f":"D51*E51","v":0}]
[null,null,{"$f":"F!C86","v":"1 - 9 m"},{"$f":"F!D86","v":0},1,{"$f":"D52*E52","v":0}]
[null,null,{"$f":"F!C87","v":"10 - 29 m"},{"$f":"F!D87","v":0},2,{"$f":"D53*E53","v":0}]
[null,null,{"$f":"F!C88","v":"30 - 49 m"},{"$f":"F!D88","v":0},3,{"$f":"D54*E54","v":0}]
[null,null,{"$f":"F!C90","v":"> 100 m"},{"$f":"F!D90","v":0},4,{"$f":"D55*E55","v":0}]
[{"$f":"F!A91","v":"F17"},{"$f":"F!B91","v":"Non-vegetated Aquatic Cover"},{"$f":"F!C91","v":"Near waters that are deeper than 0.5 m, the cover for fish, aquatic invertebrates, and/or amphibians that is provided by horizontally incised banks and/or partly-submerged accumulations of wood thicker than 10 cm (NOT by living vegetation) is:"},null,null,null,{"$f":"IF((AllSat+AllSat>0),\"\",IF((OpenW=0),\"\", IF((SmallAA=1),\"\", MAX(F57:F59)/MAX(E57:E59))))","v":""},"WoodAbove11","Large woody debris helps protect frogs and aquatic salamanders from aerial predators, and provides important basking sites. In calculations, is excluded automatically (cell goes blank) if wetland never has surface water during an average year, or has no open water, or  is <0.01 ha."]
[null,null,{"$f":"F!C92","v":"Little or none, or all water is shallower than 0.5 m most of the year."},{"$f":"F!D92","v":0},0,{"$f":"D57*E57","v":0}]
[null,null,{"$f":"F!C93","v":"Intermediate"},{"$f":"F!D93","v":0},1,{"$f":"D58*E58","v":0}]
[null,null,{"$f":"F!C94","v":"Extensive"},{"$f":"F!D94","v":0},2,{"$f":"D59*E59","v":0}]
[{"$f":"F!A95","v":"F18"},{"$f":"F!B95","v":"Interspersion of Robust Emergents & Open Water"},{"$f":"F!C95","v":"During most of the growing season, the spatial pattern of tall robust herbaceous vegetation (e.g., cattail, bulrush) that has surface water beneath it is mostly:"},null,null,null,{"$f":"IF((AllSat+AllSat>0),\"\",IF((NoPonded=1),\"\",IF((NoOpenPonded+NoOpenPonded1>0),\"\",IF((AllOpenPond=1),\"\", IF((SmallAA=1),\"\", MAX(F61:F63)/MAX(E61:E63))))))","v":0},"Interspers11","Unshaded open water areas potentially provide warmer conditions favored by many amphibians, while nearby areas with cover provide protection from predators. In calculations, is excluded automatically (cell goes blank) if wetland never has surface water during an average year, if no ponded water, if ponded water but no vegetation, if ponded but no open water, or if <0.01 ha."]
[null,null,{"$f":"F!C96","v":"Scattered in small clumps, islands, or patches throughout the surface water area."},{"$f":"F!D96","v":0},3,{"$f":"D61*E61","v":0}]
[null,null,{"$f":"F!C97","v":"Intermediate"},{"$f":"F!D97","v":0},2,{"$f":"D62*E62","v":0}]
[null,null,{"$f":"F!C98","v":"Clumped at one or a few sides of the surface water area, or mostly surrounds a central area of open water.  Or such vegetation is absent or covers <9 sq m and <1% of the AA."},{"$f":"F!D98","v":0},1,{"$f":"D63*E63","v":0}]
[{"$f":"F!A101","v":"F21"},{"$f":"F!B101","v":"Stained Surface Water"},{"$f":"F!C101","v":"Most surface water is tea-colored (from tannins, not iron bacteria or silt), and/or its pH is usually <5.5. Nearby vegetation is mostly moss and/or conifers. "},{"$f":"F!D101","v":0},null,null,{"$f":"IF((D64=1), 0,\"\")","v":""},"Stained11","Stained surface waters tend to be less biologically productive and thus less supportive in the early development of pond-breeding amphibians.  Is excluded from calculations (cell goes blank) automatically if wetland is <0.01 ha."]
[{"$f":"F!A102","v":"F22"},{"$f":"F!B102","v":"Fish"},{"$f":"F!C102","v":"Fish (native or stocked) are known to be present in the AA.  Or fish can access at least part of the AA during one or more days annually.  If uncertain, use answer from Form OF, item  OF15, or enter \"0\"."},{"$f":"F!D102","v":0},null,null,{"$f":"IF((AllSat+AllSat>0),\"\", IF((SmallAA=1),\"\", 1-D65))","v":1},"Fish11","Populations of some amphibians (e.g., four-toed salamander) seem to thrive best in fishless wetlands. Predatory fish (especially, exotic species) can cause extirpations of native species (Pearl et al. 2005). However, wood frogs in Alberta foothill wetlands may be relatively unharmed if the fish that are present are only native (not stocked) species (Schank et al. 2011)."]
[{"$f":"F!A103","v":"F23"},{"$f":"F!B103","v":"Beaver Probability"},{"$f":"F!C103","v":"Use of the AA by beaver during the past 5 years is (select most applicable ONE):"},null,null,null,{"$f":"IF((AllSat+AllSat>0),\"\",MAX(F67:F70)/MAX(E67:E70))","v":0},"Beaver11","Beaver dam-building activities are highly beneficial to amphibian habitat, creating warmer stagnant pools and increasing the overall productivity of river systems.  Beaver ponds provide abundant submersed vegetation for attachment of eggs of frogs and salamanders, as well as cover for adults.  Presence of wood frog is highly correlated with beaver flowages in some parts of Alberta (Stevens et al. 2006, 2007). (Stevens et al. 2006, 2007).  In calculations, is excluded automatically (cell goes blank) if wetland never has surface water during an average year."]
[null,null,{"$f":"F!C104","v":"evident from direct observation or presence of gnawed limbs, dams, tracks, dens, lodges, or extensive stands of water-killed trees (snags)."},{"$f":"F!D104","v":0},4,{"$f":"D67*E67","v":0}]
[null,null,{"$f":"F!C105","v":"likely based on known occurrence in the region and proximity to suitable habitat, which may include: (a) a persistent freshwater wetland, pond, or lake, or a perennial low or mid-gradient (<10%) channel, and (b) a corridor or multiple stands of hardwood trees and shrubs in vegetated areas near surface water."},{"$f":"F!D105","v":0},3,{"$f":"D68*E68","v":0}]
[null,null,{"$f":"F!C106","v":"unlikely because site characteristics above are deficient, and/or this is a settled area or other area where beaver are routinely removed.  But beaver occur in this part of the region (i.e., within 25 km)."},{"$f":"F!D106","v":0},1,{"$f":"D69*E69","v":0}]
[null,null,{"$f":"F!C107","v":"none.  Beaver are absent from this part of the region."},{"$f":"F!D107","v":0},0,{"$f":"D70*E70","v":0}]
[{"$f":"F!A125","v":"F28"},{"$f":"F!B125","v":"Groundwater: Strength of Evidence"},{"$f":"F!C125","v":"Select first applicable choice. "},null,null,null,{"$f":"IF((D74=1),\"\",MAX(F71:F74)/MAX(E72:E74))","v":0},"GroundW11","Wetlands with substantial groundwater inputs tend to have more stable and reliable water levels, thus increasing the likelihood of amphibians breeding successfully.  Also, winter water temperatures are warmer than most receiving surface waters.  However, the cooler temperatures in summer associated with groundwater input may be less favorable to development of some amphibians. In calculations, is excluded automatically (cell goes blank) if no evidence of groundwater influx; otherwise is rated based on response in column D."]
[null,null,{"$f":"F!C126","v":"Groundwater monitoring has demonstrated that groundwater primarily discharges to the wetland for longer periods during the year than periods when the wetland recharges the groundwater.  Or, springs are known to be present within the AA.\n\n\n"},{"$f":"F!D126","v":0},3,{"$f":"D72*E72","v":0}]
[null,null,{"$f":"F!C127","v":"One or more of the following are true: (a) the upper end of the AA is located very close to the base of (but mostly not ON) a natural slope much steeper (usually >15%) than that within the AA and longer than 100 m, OR\n(b) rust deposits (\"iron floc\"), colored precipitates, or dispersible natural oil sheen are prevalent in the AA, OR\n(c) AA water is remarkably clear in contrast to naturally stained waters typical in nearby wetlands, OR\n(d) AA is located at a geologic fault.\n\n"},{"$f":"F!D127","v":0},2,{"$f":"D73*E73","v":0}]
[null,null,{"$f":"F!C128","v":"Neither of above is true, although some groundwater may discharge to or flow through the AA.  Or groundwater influx is unknown."},{"$f":"F!D128","v":0},0,{"$f":"D74*E74","v":0}]
[{"$f":"F!A129","v":"F29"},{"$f":"F!B129","v":"Internal Gradient"},{"$f":"F!C129","v":"The gradient along most of the flow path within the AA is:"},null,null,null,{"$f":"MAX(F76:F79)/MAX(E76:E79)","v":0},"Gradient11","Most amphibians in this region appear to prefer ponded or slowly-flowing waters, as are typically associated with gentle gradient.  "]
[null,null,{"$f":"F!C130","v":"<2%, or, no slope is ever apparent (i.e., flat). Or, the wetland is in a depression or pond with no inlet and no outlet."},{"$f":"F!D130","v":0},4,{"$f":"D76*E76","v":0}]
[null,null,{"$f":"F!C131","v":"2-5%"},{"$f":"F!D131","v":0},3,{"$f":"D77*E77","v":0}]
[null,null,{"$f":"F!C132","v":"6-10%"},{"$f":"F!D132","v":0},2,{"$f":"D78*E78","v":0}]
[null,null,{"$f":"F!C133","v":">10%"},{"$f":"F!D133","v":0},0,{"$f":"D79*E79","v":0}]
[{"$f":"F!A140","v":"F31"},{"$f":"F!B140","v":"Interspersion of Herbaceous and Woody Cover"},{"$f":"F!C140","v":"The following best represents the distribution pattern of woody vegetation VS. unshaded herbaceous/ moss vegetation within the AA:"},null,null,null,{"$f":"MAX(F81:F84)/MAX(E81:E84)","v":0},"HerbWoodMix11","A well-interspersed mixture of herbaceous and woody vegetation is hypothesized to be most beneficial to amphibians because it provides both a moist microclimate and warmer open areas in close proximity."]
[null,null,{"$f":"F!C141","v":"(a) Woody cover and herbaceous/ moss cover EACH comprise 30-70% of the vegetated part of the AA, AND (b) There are many patches of woody vegetation scattered widely within herbaceous/ moss vegetation, or many patches of herbaceous vegetation scattered widely within woody vegetation."},{"$f":"F!D141","v":0},3,{"$f":"D81*E81","v":0}]
[null,null,{"$f":"F!C142","v":"(a) Woody cover and herbaceous/ moss EACH comprise 30-70% of the vegetated AA, AND (b) There are few patches (\"islands\") of woody vegetation scattered widely within herbaceous vegetation, or few patches of herbaceous/ moss vegetation (\"gaps\") scattered widely within woody vegetation."},{"$f":"F!D142","v":0},2,0]
[null,null,{"$f":"F!C143","v":"(a) Woody cover OR herbaceous/ moss comprise >70% of the vegetated AA, AND (b) There are several patches of the other scattered within it. "},{"$f":"F!D143","v":0},1,0]
[null,null,{"$f":"F!C144","v":"(a) Woody cover OR herbaceous/ moss comprise >70% of the vegetated AA, AND (b) The other is absent or is mostly in a single area or distinct zone with almost no intermixing of woody and unshaded herbaceous/ moss vegetation."},{"$f":"F!D144","v":0},0,0]
[{"$f":"F!A151","v":"F33"},{"$f":"F!B151","v":"Woody Diameter Classes"},{"$f":"F!C151","v":"Mark all the classes of woody plants within the AA, but only IF they comprise more than 5% of the woody canopy within the AA.  Do not count trees that adjoin but are not within the AA."},null,null,null,{"$f":"IF((NoWoodyVeg=1),\"\",IF((NoTrees=1),\"\",((SUM(D86:D93)/8+ MAX(F86:F93)/MAX(E86:E93))/2)))","v":0},"TreeVar11","During certain months of the year many salamanders and some frogs and toads require the moist microclimate and abundant invertebrate foods found in or under large downed in the uplands surrounding wetlands.  Forests with large-diameter trees are most likely to have such conditions.  However, the branches of smaller-diameter shrubs when partially inundated provide suitable sites for attachment of aquatic salamander egg masses. The dominant type of vegetation, both near a stream and in a watershed generally,  has the potential to strongly influence aquatic productivity (Ball et al. 2010).  In calculations, is excluded automatically (cell goes blank) if trees occupy <5% of the vegetated part of the AA. Otherwise, score is based on the number of categories and the presence of the categories with the greatest weights, i.e., larger trees."]
[null,null,{"$f":"F!C152","v":"coniferous, 1-9 cm diameter and >1 m tall"},{"$f":"F!D152","v":0},1,{"$f":"D86*E86","v":0}]
[null,null,{"$f":"F!C153","v":"broad-leaved deciduous 1-9 cm diameter and >1 m tall"},{"$f":"F!D153","v":0},1,0]
[null,null,{"$f":"F!C154","v":"coniferous, 10-19 cm diameter"},{"$f":"F!D154","v":0},2,0]
[null,null,{"$f":"F!C155","v":"broad-leaved deciduous 10-19 cm diameter"},{"$f":"F!D155","v":0},2,0]
[null,null,{"$f":"F!C156","v":"coniferous, 20-40 cm diameter"},{"$f":"F!D156","v":0},3,0]
[null,null,{"$f":"F!C157","v":"broad-leaved deciduous 20-40 cm diameter"},{"$f":"F!D157","v":0},3,0]
[null,null,{"$f":"F!C158","v":"coniferous, >40 cm diameter"},{"$f":"F!D158","v":0},4,0]
[null,null,{"$f":"F!C159","v":"broad-leaved deciduous >40 cm diameter"},{"$f":"F!D159","v":0},4,0]
[{"$f":"F!A160","v":"F34"},{"$f":"F!B160","v":"Downed Wood"},{"$f":"F!C160","v":"The number of downed wood pieces longer than 2 m and with diameter >10 cm, and not persistently submerged, is:"},null,null,null,{"$f":"IF((NoTrees=1),\"\", MAX(F95:F96))","v":0},"WoodDown11","Downed wood provides food, cover, and a stable microclimate for many salamanders. In calculations, is excluded automatically (cell goes blank) if woody vegetation is <5% of the vegetated part of the AA."]
[null,null,{"$f":"F!C161","v":"Several ( >5 if AA is >5 hectares, less for smaller AAs)"},{"$f":"F!D161","v":0},1,{"$f":"D95*E95","v":0}]
[null,null,{"$f":"F!C162","v":"Few or none "},{"$f":"F!D162","v":0},0,{"$f":"D96*E96","v":0}]
[{"$f":"F!A200","v":"F42"},{"$f":"F!B200","v":"Ground Irregularity"},{"$f":"F!C200","v":"Consider the parts of the AA that lack surface water at some time of the year.  Excluding slash from logging, the number of small pits, raised mounds, hummocks, boulders, upturned trees, animal burrows, gullies, natural levees, wide soil cracks, and microdepressions is:"},null,null,null,{"$f":"MAX(F98:F100)/MAX(E98:E100)","v":0},"Girreg11","Complex microtopography provides many suitable microclimates important to survival of adult amphibians during the late summer, fall, and winter (e.g., Browne & Pazkowski 2010)."]
[null,null,{"$f":"F!C201","v":"Few or none (minimal microtopography; <1% of that area) "},{"$f":"F!D201","v":0},0,{"$f":"D98*E98","v":0}]
[null,null,{"$f":"F!C202","v":"Intermediate"},{"$f":"F!D202","v":0},1,{"$f":"D99*E99","v":0}]
[null,null,{"$f":"F!C203","v":"Several (extensive micro-topography)"},{"$f":"F!D203","v":0},2,{"$f":"D100*E100","v":0}]
[{"$f":"F!A249","v":"F52"},{"$f":"F!B249","v":"Natural Cover in Buffer"},{"$f":"F!C249","v":"Along the wetland-upland edge and extending 30 m upslope, the percentage of the upland that contains natural (not necessarily native -- see column E) land cover taller than 10 cm is:"},null,null,null,{"$f":"MAX(F102:F106)/MAX(E102:E106)","v":0},"BuffNatPct11","To meet all their life history requirements, most amphibians require uplands in close proximity to, or interspersed within, suitable wetlands.  Uplands that are dominated by natural vegetation usually provide the most suitable microclimates and habitat structure.  When radiotracked frogs on Vancouver Island were released inside clusters of trees amidst otherwise unsuitable habitat (clearcuts), the proportion of frogs abandoning the tree cluster was greater the smaller the cluster.  Frogs were less likely to leave tree patches intersected by a running stream or where neighborhood stream density was high.  Scattered tree patches of 2.0 to 3.7 acres, preferably in stream locations, were the minimum needed to allow successful overland passage of one frog species (Chan-McLeod & Moy 2007).  However, as noted by Cushman (2006), “The suggestion that forest cover in the [buffer] landscape benefits amphibians may not apply to all species that are fully aquatic or that depend on nonforested upland habitat.”  Also, in Oregon Pearl et al. (2005) found only one of five amphibian species to be correlated with surrounding forest cover, and another one of the amphibians (Pacific treefrog) was negatively correlated with it. "]
[null,null,{"$f":"F!C250","v":"<5% "},{"$f":"F!D250","v":0},0,{"$f":"D102*E102","v":0}]
[null,null,{"$f":"F!C251","v":"5 to 30%"},{"$f":"F!D251","v":0},3,{"$f":"D103*E103","v":0}]
[null,null,{"$f":"F!C252","v":"30 to 60%"},{"$f":"F!D252","v":0},4,{"$f":"D104*E104","v":0}]
[null,null,{"$f":"F!C253","v":"60 to 90%"},0,7,{"$f":"D105*E105","v":0}]
[null,null,{"$f":"F!C254","v":">90%.  SKIP to F54 (Cliffs)."},{"$f":"F!D254","v":0},10,{"$f":"D106*E106","v":0}]
[{"$f":"F!A280","v":"F59"},{"$f":"F!B280","v":"Unvisited Core Area "},{"$f":"F!C280","v":"The percentage of the AA almost never visited by humans during an average growing season probably comprises: [Note: Do not include visitors on trails outside of the AA unless more than half the wetland is visible from the trails and they are within 30 m of the wetland edge.  In that case, imagine the percentage of the AA that would be covered by the trail if it were placed within the AA.]"},null,null,null,{"$f":"MAX(F108:F113)/MAX(E108:E113)","v":0},"Core1_11","Increased visitation by humans and pets can potentially increase the spread of aquatic fungi that are lethal to many amphibians."]
[null,null,{"$f":"F!C281","v":"<5% and no inhabited building is within 100 m of the AA"},{"$f":"F!D281","v":0},1,{"$f":"D108*E108","v":0}]
[null,null,{"$f":"F!C282","v":"<5% and inhabited building is within 100 m of the AA"},{"$f":"F!D282","v":0},0,0]
[null,null,{"$f":"F!C283","v":"5-50% and no inhabited building is within 100 m of the AA"},{"$f":"F!D283","v":0},3,0]
[null,null,{"$f":"F!C284","v":"5-50% and inhabited building is within 100 m of the AA"},{"$f":"F!D284","v":0},2,0]
[null,null,{"$f":"F!C285","v":"50-95%"},{"$f":"F!D285","v":0},4,0]
[null,null,{"$f":"F!C286","v":">95% of the AA"},{"$f":"F!D286","v":0},5,0]
[{"$f":"F!A287","v":"F60"},{"$f":"F!B287","v":"Frequently Visited Area"},{"$f":"F!C287","v":"The percentage of the AA visited by humans almost daily for several weeks during an average growing season probably comprises: [Note: Do not include visitors on trails outside of the AA unless more than half the wetland is visible from the trails and they are within 30 m of the wetland edge.   In that case, imagine the percentage of the AA that would be covered by the trail if it were placed within the AA.]"},null,null,null,{"$f":"MAX(F115:F118)/MAX(E115:E118)","v":0},"Core2_11","See above."]
[null,null,{"$f":"F!C288","v":"<5%.  If F59 was answered \">95%\", SKIP to F63 (Consumptive Uses)."},{"$f":"F!D288","v":0},3,{"$f":"D115*E115","v":0}]
[null,null,{"$f":"F!C289","v":"5-50%"},{"$f":"F!D289","v":0},2,{"$f":"D116*E116","v":0}]
[null,null,{"$f":"F!C290","v":"50-95%"},{"$f":"F!D290","v":0},1,{"$f":"D117*E117","v":0}]
[null,null,{"$f":"F!C291","v":">95% of the AA"},{"$f":"F!D291","v":0},0,{"$f":"D118*E118","v":0}]
[{"$f":"F!A293","v":"F62"},{"$f":"F!B293","v":"BMP - Wildlife Protection"},{"$f":"F!C293","v":"Fences, observation blinds, platforms, paved trails, exclusion periods, and/or well-enforced prohibitions on motorized boats, off-leash pets, and off road vehicles appear to effectively exclude or divert visitors and their pets from the AA at critical times in order to minimize disturbance of wildlife (except during hunting seasons).  Enter \"1\" if true. "},{"$f":"F!D293","v":0},null,null,{"$f":"IF((D113+D115>1),\"\",D119)","v":0},"BMP_11","Excessive human traffic and free-roaming pets can harm native amphibians directly (collecting and predation) and indirectly (habitat alteration), so measures to reduce such impacts are given credit.  \\  In calculations, is excluded automatically (cell goes blank) if last choice in F59 was chosen AND first choice in F60 was chosen."]
[{"$f":"F!A307","v":"F65"},{"$f":"F!B307","v":"Salinity, Alkalinity, Conductance "},{"$f":"F!C307","v":"Based on measurement from a surface water area larger than .01 hectare, the AA's surface water is mostly:"},null,null,null,{"$f":"IF((D124=1),\"\",IF((D121=1),0,\"\"))","v":""},"Salin11","Productivity of most amphibian species is greater in fresh rather than saline water, and some species are absent from high-conductivity waters (Browne et al. 2009).  Wood frog eggs and hatchlings are harmed when salt concentrations exceed 4500 mg/L (Langhans et al. 2009, Petranka et al. 2010), or perhaps as little as 78 mg/L (Sanzo & Hecnar 2006). If wetland is saline or brackish the score for this indicator is 0.  Otherwise it is ignored in the calculations."]
[null,null,{"$f":"F!C308","v":"Brackish or saline (conductance of >25 mS/cm, or >5000 ppm TDS). Or plants that indicate saline conditions comprise >20% of ground cover.  Trees and shrubs mostly absent.  Salt crust obvious around the perimeter and on flats."},{"$f":"F!D308","v":0},0,{"$f":"D121*E121","v":0}]
[null,null,{"$f":"F!C309","v":"Slightly brackish (conductance of 2.5- 25 mS/cm, or 500 - 5000 ppm TDS).  Or plants that indicate saline conditions comprise 1-20% of ground cover.  Salt crust may or may not be present along perimeter."},{"$f":"F!D309","v":0},1,{"$f":"D122*E122","v":0}]
[null,null,{"$f":"F!C310","v":"Fresh (conductance of < 2.5 mS/cm, or <500 ppm TDS). Plants that indicate saline conditions are sparse or absent. No salt crust along perimeter."},{"$f":"F!D310","v":0},2,{"$f":"D123*E123","v":0}]
[null,null,{"$f":"F!C311","v":"Unknown condition (was not measured because surface water absent or insufficient, or measurement conflicted with plant indicators). "},{"$f":"F!D311","v":0}]
[{"$f":"F!A312","v":"F66"},{"$f":"F!B312","v":"Water Quality Problem Area Located Upslope"},{"$f":"F!C312","v":"Sampling indicates problems with the quality of surface waters or sediment within the AA, or within 5 km upstream or upslope, as caused by (enter 1 for ALL that apply):"},null,null,null,{"$f":"IF((D130=1), \"\", MAX(D127:D129))","v":0},"WQprob11","Excessive suspended sediment can interfere with the respiration and reproduction of larval amphibians (Knutson et al. 2004). High levels of some substances from livestock use or wastewater effluent can harm amphibian populations and reduce amphibian diversity, e.g., Schmutzer et al. 2008)."]
[null,null,{"$f":"F!C313","v":"nutrients (phosphorus, nitrate, ammonia), or a water body within 5 km that contributes to the AA has been labeled \"hyper-eutrophic\" based on excessive levels of either total phosphorus or chlorophyll-a."},{"$f":"F!D313","v":0}]
[null,null,{"$f":"F!C314","v":"suspended sediment or turbidity"},{"$f":"F!D314","v":0}]
[null,null,{"$f":"F!C315","v":"metals (mercury, lead, zinc, copper, cadmium, others)"},{"$f":"F!D315","v":0}]
[null,null,{"$f":"F!C316","v":"petrochemicals (pesticides, herbicides, PCBs, others)"},{"$f":"F!D316","v":0}]
[null,null,{"$f":"F!C317","v":"None of above, or no data. "},{"$f":"F!D317","v":0}]
[{"$f":"F!A328","v":"F69"},{"$f":"F!B328","v":"Plants or Animals of Conservation Concern"},{"$f":"F!C328","v":"If required, survey the AA for plant or animal species believed to be of conservation concern in Alberta (see list on Form F in Appendix A of Manual).  Do so at appropriate times of the year, especially if the data review conducted during the office phase of this assessment indicated their past presence in the general vicinity.  If you do detect these species or have reliable knowledge of their recent (within ~5 years) occurrence within the AA, indicate that below.  "},null,null,null,null,"RareAmphib","Because of their relative rarity, these amphibian species contribute more to regional biodiversity than amphibian species with broader habitat tolerances."]
[null,null,{"$f":"F!C331","v":"One or more of the rare amphibian species was detected within the AA."},{"$f":"F!D331","v":0},null,null,{"$f":"IF((D132=1),1,\"\")","v":""}]
[{"$f":"S!A18","v":"S6"},{"$f":"S!B18","v":"Accelerated Inputs of Contaminants and/or Salts"},null,{"$f":"S!F32","v":0},null,null,{"$f":"1-D133","v":1},"Toxic11","Larval amphibians (tadpoles) are very sensitive to pesticides and many other toxins, e.g., Pollett & Bendell-Young 2000.  Tiger salamanders were harmed by concentrations of 75 and 250 mu g/L atrazine, an herbicide commonly applied near Alberta wetlands (Larson et al 1998).  "]
[]
[null,null,"Aquatic Habitat Structure [HabStrucA]"]
[null,"Wetlands <10 hectares:","AVERAGE(WetPerim2Area, WetVegArea, OWpct11,  Interspers11, ClassRichIn, HerbWoodMix11, IsoWet11, Girreg11, Vwidth11, TreeVar11, WoodDown11, WoodAbove11)",null,null,null,{"$f":"IF((GT10HA=1),G137,IFERROR(AVERAGE(WetPerim2Area, WetVegArea, OWpct11,  Interspers11, ClassRichIn,ISOwet11, Girreg11, Vwidth11, TreeVar11, WoodDown11, WoodAbove11),\"\"))","v":0}]
[null,"Wetlands >10 hectares:","Substituted OWpct, MixWaterVeg, MixHerbWood",null,null,null,{"$f":"IFERROR(AVERAGE(WetPerim2Area, WetVegArea, OWpct_AM, MixWaterVeg, ClassRichIn, ISOwet11, Girreg11, Vwidth11, TreeVar11, WoodDown11, WoodAbove11),\"\")","v":0}]
[]
[null,null,"Aquatic Productivity [CfixA]"]
[null,null,"AVERAGE(Salin11, AVERAGE(GrowDD, Spring, MarshPct, ClassRich1k, GroundW11, Beaver11, Gradient11, SatPct11, Fluctu11)  ",null,null,null,{"$f":"IFERROR(AVERAGE(Salin11, AVERAGE(GrowDD, Spring, ClassRich1k, GroundW11, Beaver11, Salin11, Gradient11, SatPct11, Fluctu11)),\"\")","v":0}]
[]
[null,null,"Reduced Predation Risk [PredA]"]
[null,null,"AVERAGE(Core1_11, Core2_11, MAX(1-FishPres, Fish11), BMP_11)",null,null,null,{"$f":"IFERROR(AVERAGE(Core1_11, Core2_11, MAX(1-FishPres,  Fish11),BMP_11),\"\")","v":0.25}]
[]
[null,null,"Stressors (lack of) [StressA]"]
[null,null,"AVERAGE(1-WQrisk, 1-WindSumm, WQprob11, Toxic11, 1-RdDens1k, DistRd, Dist2DevCrop)",null,null,null,{"$f":"IFERROR(AVERAGE(1-WQrisk, 1-WindSumm, WQprob11, Toxic11, 1-RdDens1k, Dist2Road, Dist2DevCrop),\"\")","v":0.8}]
[]
[null,null,"ABWRET-A FUNCTION MODEL"]
[null,null,"Amphibian Habitat"]
[null,null,"AVERAGE(SensAm, RareAmphib,MarshPct,  UniqClass, AVERAGE(HabStrucA, CfixA, PredA,StressA), WetDens1k, PerimNatCov)",null,null,null,{"$f":"10*AVERAGE(SensAm, RareAmphib,UniqClass, MarshPct, AVERAGE(HabStrucA1a, CfixA1a, PredA1a, StressA1a), WetDens1k_NoBog, PerimNatCov)","v":2.625}]
[null,null,null,null," ",null,null,null,"Literature Cited"]
[null,null,"ABWRET-E model:",null,null,null,null,null,"Ball, B.A., J.S. Kominoski, H.E. Adams, S.E. Jones, E.S. Kane, T.D. Loecke, W.M. Mahaney, J.P. Martina, C.M. Prather, T.M.P. Robinson, and C.T. Solomon. 2010. Direct and terrestrial vegetation-mediated effects of environmental change on aquatic ecosystem processes. Bioscience 60:590-601."]
[null,1,"Calculate these averages:",null,null,null,null,null,"Bender, D. J., L. Tischendorf, and L. Fahrig. 2003. Evaluation of patch isolation metrics for predicting animal movement in binary landscapes. Landscape Ecology 18:17-39."]
[null,"a","AVERAGE(MixWaterVeg, OWpct) ",{"$f":"IFERROR(AVERAGE(MixWaterVeg, OWpct_AM),\"\")","v":""},null,null,null,null,"Browne, C. L., C. A. Paszkowski, A. L. Foote, A. Moenting, and S. M. Boss. 2009. The relationship of amphibian abundance to habitat features across spatial scales in the Boreal Plains. Ecoscience 16:209-223."]
[null,"b","AVERAGE (MixHerbWood, ClassRichIn) ",{"$f":"IFERROR(AVERAGE(MixHerbWood, ClassRichIn),\"\")","v":""},null,null,null,null,"Browne, C. L., and C. A. Paszkowski. 2010. Hibernation sites of western toads (Anaxyrus boreas): Characterization and management implications. Herpetological Conservation and Biology 5.1:49-63."]
[null,"c","AVERAGE(ClassRich1k, WetDens1k_NoBog), ",{"$f":"IFERROR(AVERAGE(ClassRich1k, WetDens1k_NoBog),\"\")","v":""},null,null,null,null,"Chan-McLeod, A. C. A. and A. Moy. 2007. Evaluating residual tree patches as stepping stones and short-term refugia for red-legged frogs. Journal of Wildlife Management 71:1836-1844."]
[null,"d","AVERAGE(Dist2DevCrop, NatCov1k, PerimNatCov)",{"$f":"IFERROR(AVERAGE(Dist2DevCrop, NatCov1k, PerimNatCov),\"\")","v":""},null,null,null,null,"Cushman, S. A. 2006. Effects of habitat loss and fragmentation on amphibians: a review and prospectus. Biological Conservation 128:231-240."]
[null,2,"10*AVERAGE (MarshPct, UniqFenMarshSwamp, a, b, c, d)",{"$f":"IFERROR(10*AVERAGE(MarshPct, UniqFenMarshSwamp,D154:D157),\"\")","v":""},null,null,null,null,"Eigenbrod, F., S. J. Hecnar, and L. Fahrig. 2008a. Accessible habitat: an improved measure of the effects of habitat loss and roads on wildlife populations. Landscape Ecology:159-168.",null,null,null," "]
[null,null,null,null,null,null,null,null,"Eigenbrod, F., S. J. Hecnar, and L. Fahrig. 2008b. The relative effects of road traffic and forest cover on anuran populations. Biological Conservation 141:35-46."]
[null,null,"ABWRET-E with substitutions:",null,null,null,null,null,"Knutson, M. G., W. B. Richardson, D. M. Reineke, B. R. Gray, J. R. Parmelee, and S. E. Weick. 2004. Agricultural ponds support amphibian populations. Ecological Applications 14:669-684."]
[null,1,"Calculate these averages:",null,null,null,null,null,"Langhans, M., B. Peterson, A. Walker, G. R. Smith, and J. E. Rettig. 2009. Effects of salinity on survivorship of wood frog (Rana sylvatica) tadpoles. Journal of Freshwater Ecology 24:335-337."]
[null,"a","AVERAGE(Interspers11, OWpct11) ",{"$f":"IFERROR(AVERAGE(Interspers11, OWpct11),\"\")","v":0},null,null,null,null,"Larson, D. L., S. McDonald, A. J. Fivizzani, W. E. Newton, and S. J. Hamilton. 1998. Effects of the herbicide atrazine on Ambystoma tigrinum metamorphosis: Duration, larval growth, and hormonal response. Physiological Zoology 71:671-679."]
[null,"b","AVERAGE (HerbWoodMix11, ClassRichIn) ",{"$f":"IFERROR(AVERAGE(HerbWoodMix11, ClassRichIn),\"\")","v":0},null,null,null,null,"Marsh, D. M. 2007. Edge effects of gated and ungated roads on terrestrial salamanders. Journal of Wildlife Management 71:389-394."]
[null,"c","AVERAGE(ClassRich1k, WetDens1k_NoBog), ",{"$f":"IFERROR(AVERAGE(ClassRich1k, WetDens1k_NoBog),\"\")","v":""},null,null,null,null,"Pearl, C., M. Adams, N. Leuthold, and R. Bury. 2005. Amphibian occurrence and aquatic invaders in a changing landscape: implications for wetland mitigation in the Willamette Valley, Oregon, USA. Wetlands 25:76-88."]
[null,"d","AVERAGE(Dist2DevCrop, NatCov1k, PerimNatCov)",{"$f":"IFERROR(AVERAGE(Dist2DevCrop, NatCov1k, PerimNatCov),\"\")","v":""},null,null,null,null,"Petranka, J. and E. Doyle. 2010. Effects of road salts on the composition of seasonal pond communities: can the use of road salts enhance mosquito recruitment? Aquatic Ecology 44:155-166."]
[null,2,"10*AVERAGE (MarshPct, UniqFenMarshSwamp, a, b, c, d)",{"$f":"10*AVERAGE(MarshPct, UniqFenMarshSwamp,D162:D165)","v":0},null,null,null,null,"Pollet, I. and L. I. Bendell-Young. 2000. Amphibians as indicators of wetland quality in wetlands forme from oil sands effluent. Environmental Toxicology and Chemistry 19:2589-2597."]
[null,null,null,null,null,null,null,null,"Sanzo, D. and S. J. Hecnar. 2006. Effects of road de-icing salt (NaCl) on larval wood frogs (Rana sylvatica). Environmental Pollution 140:247-256."]
[null,null,null,null,null,null,null,null,"Schmutzer, A. C., M. J. Gray, E. C. Burton, and D. L. Miller. 2008. . Impacts of cattle on amphibian larvae and the aquatic environment. Freshwater Biology 53:2613-2625."]
[null,null,null,null,null,null,null,null,"Semlitsch, R. D., T. J. Ryan, K. Ramed, M. Chatfield, B. Drehman, N. Pekarek, M. Spath, and A. Watland. 2007. Salamander abundance along road edges and within abandoned logging roads in Appalachian forests. Conservation Biology 21:159-167."]
[null,null,null,null,null,null,null,null,"Stevens, C. E., C. A. Paszkowski, and A. L. Foote. 2007. Beaver (Castor canadensis) as a surrogate species for conserving anuran amphibians on boreal streams in Alberta, Canada. Biological Conservation 134:1-13."]
[null,null,null,null,null,null,null,null,"Stevens, C. E., C. A. Paszkowski, and G. J. Scrimgeour. 2006. Older is better: Beaver ponds on boreal streams as breeding habitat for the wood frog. Journal of Wildlife Management 70:1360-1371."]
[null,null,null,null,null,null,null,null,"Schank, C. M. M., C. A. Paszkowski, W. M. Tonn, and G. J. Scrimgeour. 2011. Stocked trout do not significantly affect wood frog populations in Boreal Foothills lakes. Canadian Journal of Fisheries and Aquatic Sciences 68:1790-1801."]

{"sheet":"WB","index":19,"n_rows":198,"n_cols":9,"rows_kept":198,"cut":false,"hidden":false,"merged":[[56,0,63,0],[56,1,63,1],[71,0,76,0],[64,1,70,1],[64,0,70,0],[83,0,86,0],[83,7,86,7],[83,1,86,1],[77,1,82,1],[71,1,76,1],[77,0,82,0],[130,8,135,8],[119,8,123,8],[124,8,129,8],[115,8,118,8],[106,8,114,8],[124,7,129,7],[130,7,135,7],[136,7,142,7],[34,7,39,7],[41,7,46,7],[47,7,51,7],[90,7,94,7],[95,7,99,7],[100,7,105,7],[106,7,114,7],[115,7,118,7],[71,7,76,7],[56,7,63,7],[64,7,70,7],[77,7,82,7],[90,8,94,8],[64,8,70,8],[83,8,86,8],[52,8,55,8],[119,7,123,7],[77,8,82,8],[95,8,99,8],[100,8,105,8],[47,8,51,8],[52,7,55,7],[71,8,76,8],[34,8,39,8],[41,8,46,8],[56,8,63,8],[41,0,46,0],[34,0,39,0],[41,1,46,1],[47,0,51,0],[52,0,55,0],[52,1,55,1],[47,1,51,1],[34,1,39,1],[0,0,0,1],[27,1,33,1],[27,0,33,0],[27,8,33,8],[22,1,26,1],[22,7,26,7],[0,4,0,8],[27,7,33,7],[22,8,26,8],[130,0,135,0],[124,0,129,0],[119,0,123,0],[119,1,123,1],[95,0,99,0],[130,1,135,1],[115,1,118,1],[95,1,99,1],[90,1,94,1],[100,1,105,1],[100,0,105,0],[115,0,118,0],[124,1,129,1],[106,0,114,0],[106,1,114,1],[90,0,94,0],[154,1,155,1],[154,0,155,0],[154,8,155,8],[136,0,142,0],[149,0,153,0],[143,1,147,1],[149,8,153,8],[143,8,147,8],[149,1,153,1],[136,1,142,1],[143,7,147,7],[149,7,153,7],[154,7,155,7],[143,0,147,0],[136,8,142,8]]}
["Waterbird          Habitat",null,"The capacity to support or contribute to an abundance or diversity of waterbirds that nest or migrate through the region.","WB"]
["#","Function Indicators from Estimator","Scoring Notes",null,null,null,"Normalised Score","Indicator Abbreviation or Formula","Rationale"]
[{"$f":"OF!A8","v":"OF7"},{"$f":"OF!C8","v":"Distance to Nearest Annual Cropland or Developed Land"}," ",null,null,null,{"$f":"IF((Dist2DevCrop=\"\"),\"\",Dist2DevCrop)","v":""},"Dist2DevCrop","Wetlands located near agricultural and developed areas are often exposed to greater amounts of pesticides and human disturbance, which can reduce productivity and use by waterbirds."]
[{"$f":"OF!A11","v":"OF10"},{"$f":"OF!C11","v":"Waterfowl Breeding Density"}," ",null,null,null,{"$f":"IF((DuckDens=\"\"),\"\",DuckDens)","v":""},"DuckDens","Wetlands surrounded by many other waterfowl-producing wetlands (in landscapes of 1000, 10,000 and 100,000 ha) are more likely to support nesting waterfowl (Forcey et al. 2011) ."]
[{"$f":"OF!A18","v":"OF17"},{"$f":"OF!C18","v":"Growing Degree Days"}," ",null,null,null,{"$f":"IF((GrowDD=\"\"),\"\",GrowDD)","v":""},"GrowDD","In boreal Alberta, both breeding and molting waterfowl densities increase with lake productivity, even in eutrophic and hypereutrophic lakes (Epners et al. 2010)."]
[{"$f":"OF!A21","v":"OF20"},{"$f":"OF!C21","v":"Important Bird Area"},"If not within a designated IBA then cell turns blank (NULL) and is ignored in calculations.",null,null,null,{"$f":"IF((IBirdArea=\"\"),\"\",IF((IBirdArea=1),1,\"\"))","v":""},"IBirdArea","These are typically areas that have been officially designated by biologists as being especially important to waterbirds."]
[{"$f":"OF!A24","v":"OF23"},{"$f":"OF!C24","v":"% of the AA that is Marsh"},null,null,null,null,{"$f":"IF((MarshPct=\"\"),\"\",MarshPct)","v":""},"MarshPct","For most waterbirds, wetlands classified as marsh tend to be the most productive."]
[{"$f":"OF!A28","v":"OF27"},{"$f":"OF!C28","v":"Interspersion Index for Internal Water & Vegetation (macroscale)"}," ",null,null,null,{"$f":"IF((MixWaterVeg=\"\"),\"\",MixWaterVeg)","v":""},"MixWaterVeg","This is one of the strongest predictors of waterbird use of wetlands.  Wetlands with a nearly even mix of vegetative cover and open water tend to support the most diverse assemblages of waterbirds.  Interspersion of patches of open water amid patches of vegetation provides waterbirds with the best access to aquatic foods, and waterbird use of such wetlands has been shown to be significantly greater (Kaminski and Prince 1981, Murkin et al. 1982, Rehm & Baldassarre 2007, Schummer et al. 2012, Bolenbaugh et al. 2011). "]
[{"$f":"OF!A34","v":"OF33"},{"$f":"OF!C34","v":"% of AA that is Open Water (macro scale, Waterbird Habitat)"},"The raw value is scored as follows: <1%=0;  1%-5%=0.4; 6-30%=0.8, 31-70%=1; 71-99%=0.6; >99%=0.2",null,null,null,{"$f":"IF((OWpct_WB=\"\"),\"\",OWpct_WB)","v":""},"OWpct_WB","See above."]
[{"$f":"OF!A35","v":"OF34"},{"$f":"OF!C35","v":"% of Wetland Perimeter Adjoined by Natural Cover"}," ",null,null,null,{"$f":"IF((PerimNatCov=\"\"),\"\",PerimNatCov)","v":""},"PerimNatCov","Dense perennial cover that adjoins wetlands, whether it is comprised of native vegetation or not (Arnold et al. 2007), is essential to many nesting ducks."]
[{"$f":"OF!A39","v":"OF38"},{"$f":"OF!C39","v":"Nesting Bird Colony, Piping Plover Water Body, or Trumpeter Swan Use Area"},"If not within area where any of these species nests, then cell turns blank (NULL) and is ignored in calculations.",null,null,null,{"$f":"IF((RareBirdUse=\"\"),\"\",IF((RareBirdUse=1),1,\"\"))","v":""},"RareBirdUse","These rare or sensitive wetland birds contribute disproportionately to regional biodiversity."]
[{"$f":"OF!A43","v":"OF42"},{"$f":"OF!C43","v":"Riparian or Floodway Location"},"If not within riparian or floodplain area then cell turns blank (NULL) and is ignored in calculations.",null,null,null,{"$f":"IF((RipFloodpl=\"\"),\"\",IF((RipFloodpl=1),1,\"\"))","v":""},"RipFloodpl","Waterbirds often follow major rivers during migration, and floodplain wetlands tend to be more productive than more isolated wetlands at higher elevations."]
[{"$f":"OF!A44","v":"OF43"},{"$f":"OF!C44","v":"Shorebird Staging Wetland "},"If not within shorebird staging area then cell turns blank (NULL) and is ignored in calculations.",null,null,null,{"$f":"IF((SBstaging=\"\"),\"\",IF((SBstaging=1),1,\"\"))","v":""},"SBstaging","Migratory shorebirds contribute to biodiversity at a continental scale and are especially sensitive to chronic disturbance.  Concentration areas have not been surveyed comprehensively but when identified by biologists, that information is used here."]
[{"$f":"OF!A55","v":"OF54"},{"$f":"OF!C55","v":"Trumpeter Swan Area"},"If not within trumpeter swan area then cell turns blank (NULL) and is ignored in calculations.",null,null,null,{"$f":"IF((TrumSwan=\"\"),\"\",IF((TrumSwan=1),1,\"\"))","v":""},"TrumSwan","See OF38 above."]
[{"$f":"OF!A56","v":"OF55"},{"$f":"OF!C56","v":"% Undeveloped Openlands Within 1km"}," ",null,null,null,{"$f":"IF((UndevOpenL1k=\"\"),\"\",UndevOpenL1k)","v":""},"UndevOpenL1k","Most waterbirds are attracted more strongly to unforested than forested landscapes, at least when those are relatively undeveloped."]
[{"$f":"OF!A58","v":"OF57"},{"$f":"OF!C58","v":"FenMarshPct/ FenMarshPct1k"}," ",null,null,null,{"$f":"IF((UniqFenMarsh=\"\"),\"\",UniqFenMarsh)","v":""},"UniqFenMarsh","If a wetland contains fen or marsh but those classes (which are most important to waterbirds) are scarce in the surrounding area, the contribution of waterbird species (that associate with those classes) to local biodiversity is likely to be greater."]
[{"$f":"OF!A60","v":"OF59"},{"$f":"OF!C60","v":"Vegetation Connectivity to Other Wetlands within 1 km"}," ",null,null,null,{"$f":"IF((VegCon1k=\"\"),\"\",VegCon1k)","v":""},"VegCon1k","Corridors can be important to ducks that must walk overland with their young to find other wetlands in which to feed or molt."]
[{"$f":"OF!A61","v":"OF60"},{"$f":"OF!C61","v":"Water Permanence Probability"}," ",null,null,null,{"$f":"IF((WatProb=\"\"),\"\",WatProb)","v":""},"WatProb","Although many waterbirds use or even prefer seasonal wetlands, wetlands whose surface water persists for all or most of a growing season provide more physical habitat for waterbirds."]
[{"$f":"OF!A62","v":"OF61"},{"$f":"OF!C62","v":"Waterfowl Staging Wetland"},"If not within waterfowl staging area then cell turns blank (NULL) and is ignored in calculations.",null,null,null,{"$f":"IF((WBstaging=\"\"),\"\",IF((WBstaging=1),1,\"\"))","v":""},"WBstaging","Staging areas for waterfowl, where they congregate prior to migrating, contribute to biodiversity at a continental scale and are especially sensitive to chronic disturbance. Staging areas have not been surveyed comprehensively but when identified by biologists, that information is used here."]
[{"$f":"OF!A66","v":"OF65"},{"$f":"OF!C66","v":"Wetland Density Within 1km (excluding those with no open water)"}," ",null,null,null,{"$f":"IF((WetDens1k_OW=\"\"),\"\",WetDens1k_OW)","v":""},"WetDens1k_OW","Waterbirds prefer landscapes where multiple wetlands are present in close proximity (Naugle et al. 2000).  This is partly so that if birds are disturbed in one area, they can fly to alternate sites that serve as refuge and which may provide different but complementary water regimes and foods.  In Nebraska, migratory shorebird abundance was greater where wetland density within 10 km was greater (Webb et al. 2010). Nest density is greater where a larger proportion of the surrounding landscape is wetlands (Arnold 2007, Austin & Buhl 2009, Devries et al. 2011).  Waterbird species richness is also greater in wetlands existing in unfragmented prairie wetland landscapes (i.e., areas with wetland complexes embedded within large expanses of upland grassland, Ball et al. 1995, Stephens et al. 2005) than in isolated wetlands of the same type embedded in landscapes dominated by croplands (Naugle et al. 2001).  However, in the southern Great Plains, wetlands in landscapes with the most other wetlands within 1 and 10 km radius had lower bird densities than those with fewer surrounding wetlands, likely because of a \"dilution\" effect from the local abundance of habitat (Tsai 2012).  In another prairie landscape, waterbird nest survival was actually lower in wetlands located in areas of high wetland density (Stephens et al. 2005). "]
[{"$f":"OF!A69","v":"OF68"},{"$f":"OF!C69","v":"Wetland Vegetated Area"}," ",null,null,null,{"$f":"IF((WetVegArea=\"\"),\"\",WetVegArea)","v":""},"WetVegArea","Larger wetlands are used disproportionately by some species of nesting waterbirds. Smaller identical wetlands of equal cumulative area probably support lower numbers and cumulative richness of waterbirds, unless they are close together and connected with corridors of undeveloped land. "]
["#","Function Indicators from Onsite Visit","Categorical Choices","Data","Weight","Data  x  Weight","Normalised Score","Indicator Abbreviation or Formula","Rationale & Scoring Notes"]
[{"$f":"F!A6","v":"F1"},{"$f":"F!B6","v":"Wetland Type - Predominant"},{"$f":"F!C6","v":"Most of the vegetated part of the AA (wetland Assessment Area) is a (select ONE):"},null,null,null,{"$f":"MAX(F24:F27)/MAX(E24:E27)","v":0},"Wettype13","Most breeding waterbirds are naturally drawn to more productive wetlands, which tend to be marshes along rivers and lakes. However, a few waterbird species that nest in this region prefer open bogs and fens."]
[{"$f":"F!A7","v":"F1.1"},null,{"$f":"F!C7","v":"Wooded Swamp"},{"$f":"F!D7","v":0},1,{"$f":"D24*E24","v":0}]
[{"$f":"F!A8","v":"F1.2"},null,{"$f":"F!C8","v":"Bog"},{"$f":"F!D8","v":0},0,{"$f":"D25*E25","v":0}]
[{"$f":"F!A9","v":"F1.3"},null,{"$f":"F!C9","v":"Fen"},{"$f":"F!D9","v":0},2,{"$f":"D26*E26","v":0}]
[{"$f":"F!A10","v":"F1.4"},null,{"$f":"F!C10","v":"Marsh or Shallow Open Water"},{"$f":"F!D10","v":0},3,{"$f":"D27*E27","v":0}]
[{"$f":"F!A17","v":"F3"},{"$f":"F!B17","v":"% Saturated Only"},{"$f":"F!C17","v":"The percentage of the AA that never contains surface water during an average year (that is, except perhaps for a few hours after snowmelt or rainstorms), but which is still a wetland, is:"},null,null,null,{"$f":"MAX(F29:F34)/MAX(E29:E34)","v":0.2},"SatPct13","Most waterbirds require some unflooded shoreline for nesting, while also needing large areas of water and emergent vegetation for feeding."]
[null,null,{"$f":"F!C18","v":"less than 1%, or <0.01 hectare (about 10 m on a side) never has surface water.  In other words, all or nearly all of the AA is inundated permanently or at least seasonally."},{"$f":"F!D18","v":0},4,{"$f":"D29*E29","v":0}]
[null,null,{"$f":"F!C19","v":"1-25% of the AA never contains surface water."},{"$f":"F!D19","v":0},5,0]
[null,null,{"$f":"F!C20","v":"25-50% of the AA never contains surface water."},{"$f":"F!D20","v":0},3,0]
[null,null,{"$f":"F!C21","v":"50-99% of the AA never contains surface water."},{"$f":"F!D21","v":0},2,0]
[null,null,{"$f":"F!C22","v":">99% of the AA never contains surface water, except for water flowing in channels and/or in pools that occupy <1% of the AA. SKIP to F26 (Channel Connection & Outflow Duration)"},1,1,1]
[null,null,{"$f":"F!C23","v":">99% of the AA never contains surface water, and AA is not intersected by channels that have flow, not even for a few days per year. SKIP to F26."},{"$f":"F!D23","v":0},0,0]
[{"$f":"F!A24","v":"F4"},{"$f":"F!B24","v":"% with Persistent Surface Water"},{"$f":"F!C24","v":"The percentage of the AA that has surface water (either ponded or flowing, either open or obscured by vegetation) during all of the growing season during most years is:"},null,null,null,{"$f":"IF((AllSat+AllSat>0),\"\", MAX(F36:F40)/MAX(E36:E40))","v":0},"PermWpct13","Surface water that persists for all or most of a year (and especially, during the early summer) provides more physical habitat for waterbirds. If no surface water persists, waterbird use can still be substantial if the wetland borders a lake or large river. In calculations, is excluded automatically (cell goes blank) if wetland never has surface water during an average year. "]
[null,null,{"$f":"F!C25","v":"less than 1%, or <0.01 hectare (whichever is less).  SKIP to F8 (% Flooded Only Seasonally)."},{"$f":"F!D25","v":0},1,{"$f":"D36*E36","v":0}]
[null,null,{"$f":"F!C26","v":"1-25% of the AA, and mostly in narrow channels and/or small scattered pools."},{"$f":"F!D26","v":0},2,{"$f":"D37*E37","v":0}]
[null,null,{"$f":"F!C28","v":"25-50% of the AA"},{"$f":"F!D28","v":0},3,{"$f":"D38*E38","v":0}]
[null,null,{"$f":"F!C29","v":"50-95% of the AA"},{"$f":"F!D29","v":0},4,{"$f":"D39*E39","v":0}]
[null,null,{"$f":"F!C30","v":">95% of the AA"},{"$f":"F!D30","v":0},3,{"$f":"D40*E40","v":0}]
[{"$f":"F!A38","v":"F7"},{"$f":"F!B38","v":"Lacustrine Wetland"},{"$f":"F!C38","v":"The AA borders a body of ponded open water whose size -- not counting the vegetated AA -- exceeds 8 hectares (about 300 x 300 m) during most of the growing season.  Enter \"1\" if true, \"0\" if false."},{"$f":"F!D38","v":0},null,null,{"$f":"IF((AllSat+AllSat>0),\"\",IF((OpenW=0),\"\",IF((NoPonded=1),\"\",1)))","v":""},"Lake13","Lacustrine wetlands are especially attractive to nesting waterbirds, partly because of the variety of foods they provide, and the refuge that the large expanse of open water provides from terrestrial predators. However, nesting waterbird use of lakes may be less if there is frequent motorboat use. If wetland is not part of a lake, then ignored in calculations rather than being counted as a negative."]
[{"$f":"F!A39","v":"F8"},{"$f":"F!B39","v":"% Flooded Only Seasonally"},{"$f":"F!C39","v":"The percentage of the AA that is covered by surface water only during the wettest time of year (and for >2 consecutive days during that time) is:"},null,null,null,{"$f":"IF((AllSat+AllSat>0),\"\",MAX(F43:F47)/MAX(E43:E47))","v":0},"SeasWpct13","Most waterbirds situate their nests on or near persistent water. However, wetlands that flood only seasonally often provide more food and cover for young."]
[null,null,{"$f":"F!C40","v":"<1%. "},{"$f":"F!D40","v":0},4,{"$f":"D43*E43","v":0}]
[null,null,{"$f":"F!C41","v":"1-25% "},{"$f":"F!D41","v":0},5,{"$f":"D44*E44","v":0}]
[null,null,{"$f":"F!C42","v":"25-50% "},{"$f":"F!D42","v":0},3,{"$f":"D45*E45","v":0}]
[null,null,{"$f":"F!C43","v":"50-95% "},{"$f":"F!D43","v":0},2,{"$f":"D46*E46","v":0}]
[null,null,{"$f":"F!C44","v":">95% "},{"$f":"F!D44","v":0},1,{"$f":"D47*E47","v":0}]
[{"$f":"F!A45","v":"F9"},{"$f":"F!B45","v":"Annual Water Fluctuation Range"},{"$f":"F!C45","v":"The annual fluctuation in surface water level within most of the parts of the AA that contain surface water is:"},null,null,null,{"$f":"IF((AllSat+AllSat>0),\"\", IF((NoSeasonal=1),\"\",MAX(F49:F52)/MAX(E49:E52)))","v":0},"Fluctu13","Large water level fluctuations during the nesting season (late spring and early summer), can flood the nests of birds that nest along wetland edges. However, annual fluctuations (described here) do not necessarily parallel propensity of water levels to fluctuate during the nesting season, and can stimulate wetland productivity. In calculations, is excluded automatically (cell goes blank) if wetland never has surface water during an average year, or if none of it floods only seasonally."]
[null,null,{"$f":"F!C46","v":"<10 cm change (stable) "},{"$f":"F!D46","v":0},0,{"$f":"D49*E49","v":0}]
[null,null,{"$f":"F!C47","v":"10 cm - 50 cm change"},{"$f":"F!D47","v":0},1,{"$f":"D50*E50","v":0}]
[null,null,{"$f":"F!C49","v":"1-2 m change"},{"$f":"F!D49","v":0},2,{"$f":"D51*E51","v":0}]
[null,null,{"$f":"F!C50","v":">2 m change"},{"$f":"F!D50","v":0},2,{"$f":"D52*E52","v":0}]
[{"$f":"F!A58","v":"F11"},{"$f":"F!B58","v":"Depth Classes - Evenness of Proportions"},{"$f":"F!C58","v":"When present, surface water in most of the AA usually consists of (select one):"},null,null,null,{"$f":"IF((AllSat+AllSat>0),\"\", IF((SmallAA=1),\"\", MAX(F54:F56)/MAX(E54:E56)))","v":0},"DepthEven13","Different waterbird species prefer different water depths, so a diversity of depth classes in a wetland is likely to support a more varied mix of waterbirds (Baschuk 2010, Baschuk et al. 2012)."]
[null,null,{"$f":"F!C59","v":"One depth class that comprises >90% of the AA’s inundated area (use the classes in the question above)."},{"$f":"F!D59","v":0},0,{"$f":"D54*E54","v":0}]
[null,null,{"$f":"F!C60","v":"One depth class that comprises 60-90% of the AA's inundated area."},{"$f":"F!D60","v":0},1,{"$f":"D55*E55","v":0}]
[null,null,{"$f":"F!C61","v":"Neither of above.  Multiple depth classes; none occupy more than 50% of the AA."},{"$f":"F!D61","v":0},2,{"$f":"D56*E56","v":0}]
[{"$f":"F!A62","v":"F12"},{"$f":"F!B62","v":"% of Water Ponded vs. Flowing "},{"$f":"F!C62","v":"The percentage of the AA's surface water that is ponded (stagnant, or flows so slowly that fine sediment is not held in suspension) during most of the time it is present, and which is either open or shaded by emergent vegetation is:"},null,null,null,{"$f":"IF((AllSat+AllSat>0),\"\", IF((SmallAA=1),\"\", MAX(F58:F64)/MAX(E58:E64)))","v":0},"ISOdry13","Most wetland birds tend to feed more in ponded areas than along channels. If these isolated pools areas persist well into the summer, they allow waterbird populations to establish more breeding territories within the site, as well as concentrating invertebrate foods. In calculations, is excluded automatically (cell goes blank) if wetland never has surface water during an average year or is <0.01 ha.."]
[null,null,{"$f":"F!C63","v":"<1% or none, or occupies <0.01 hectare cumulatively.  Nearly all water is flowing.  Enter \"1\" and SKIP to F21 (Stained Surface Water)."},{"$f":"F!D63","v":0},0,{"$f":"D58*E58","v":0}]
[null,null,{"$f":"F!C64","v":"1-5% of the water, and mainly in small pools.  The rest is flowing."},{"$f":"F!D64","v":0},1,0]
[null,null,{"$f":"F!C65","v":"1-5% of the water, and mainly in a single large pool or pond.  The rest is flowing."},{"$f":"F!D65","v":0},2,0]
[null,null,{"$f":"F!C66","v":"5-30% of the water"},{"$f":"F!D66","v":0},3,0]
[null,null,{"$f":"F!C67","v":"30-70% of the water"},{"$f":"F!D67","v":0},4,0]
[null,null,{"$f":"F!C68","v":"70-95% of the water"},{"$f":"F!D68","v":0},5,0]
[null,null,{"$f":"F!C69","v":">95% of the water.  Little or no visibly flowing water within the AA."},{"$f":"F!D69","v":0},6,0]
[{"$f":"F!A71","v":"F14"},{"$f":"F!B71","v":"% of Ponded Water That Is Open "},{"$f":"F!C71","v":"In ducks-eye aerial view, the percentage of the ponded water that is open (lacking emergent vegetation during most of the growing season, and unhidden by a forest or shrub canopy) is:"},null,null,null,{"$f":"IF((AllSat+AllSat>0),\"\", IF((NoPonded=1),\"\", IF((SmallAA=1),\"\", MAX(F66:F71)/MAX(E66:E71))))","v":0},"OWpct13","Submersed and partly submersed vegetation is an essential food for many duck species, either directly or because of the higher densities of invertebrate foods that it supports (Epners et al. 2010). In calculations, is excluded automatically (cell goes blank) if wetland never has surface water during an average year.  Also is excluded automatically if wetland has no ponded water or is <0.01 ha.."]
[null,null,{"$f":"F!C72","v":"<1% or none, or largest pool occupies <0.01 hectares.  Enter \"1\" and SKIP to F20 (Floating Algae & Duckweed)."},{"$f":"F!D72","v":0},1,{"$f":"D66*E66","v":0}]
[null,null,{"$f":"F!C73","v":"1-5% of the ponded water.  Enter \"1\" and SKIP to F20."},{"$f":"F!D73","v":0},2,0]
[null,null,{"$f":"F!C74","v":"5-30% of the ponded water."},{"$f":"F!D74","v":0},4,0]
[null,null,{"$f":"F!C75","v":"30-70% of the ponded water."},{"$f":"F!D75","v":0},6,0]
[null,null,{"$f":"F!C76","v":"70-99% of the ponded water."},{"$f":"F!D76","v":0},4,0]
[null,null,{"$f":"F!C77","v":"100% of the ponded water. "},{"$f":"F!D77","v":0},3,0]
[{"$f":"F!A78","v":"F15"},{"$f":"F!B78","v":"Flat Shoreline Extent"},{"$f":"F!C78","v":"The length of the AA's shoreline (along its ponded open water) that is bordered by areas that are nearly flat (a slope less than about 5%) is:"},null,null,null,{"$f":"IF((AllSat+AllSat>0),\"\",IF((OpenW=0),\"\", IF((SmallAA=1),\"\", MAX(F73:F77)/MAX(E73:E77))))","v":""},"ShoreSlope13","A gentle shore slope provides waterbirds with easier access to upland nesting cover near the water.  In calculations, is excluded automatically (cell goes blank) if wetland never has surface water during an average year. Also is excluded automatically if wetland lacks open water or is <0.01 ha."]
[null,null,{"$f":"F!C79","v":"<1%"},{"$f":"F!D79","v":0},0,{"$f":"D73*E73","v":0}]
[null,null,{"$f":"F!C80","v":"1-25%"},{"$f":"F!D80","v":0},1,{"$f":"D74*E74","v":0}]
[null,null,{"$f":"F!C81","v":"25-50%"},{"$f":"F!D81","v":0},2,{"$f":"D75*E75","v":0}]
[null,null,{"$f":"F!C82","v":"50-75%"},{"$f":"F!D82","v":0},3,{"$f":"D76*E76","v":0}]
[null,null,{"$f":"F!C83","v":">75%"},{"$f":"F!D83","v":0},4,{"$f":"D77*E77","v":0}]
[{"$f":"F!A84","v":"F16"},{"$f":"F!B84","v":"Predominant Width of Vegetated Zone within Wetland"},{"$f":"F!C84","v":"At the driest time of year (or lowest water level), the average width of vegetated area in the AA that separates adjoining uplands from open water within the AA is:"},null,null,null,{"$f":"IF((AllSat+AllSat>0),\"\",IF((OpenW=0),\"\", IF((SmallAA=1),\"\", MAX(F79:F83)/MAX(E79:E83))))","v":""},"VwidthAbs13","Waterbird nests located in narrow wetlands may be more vulnerable to predation.  In calculations, is excluded automatically (cell goes blank) if wetland never has surface water during an average year or if wetland lacks open water or is <0.01 ha."]
[null,null,{"$f":"F!C85","v":"<1 m"},{"$f":"F!D85","v":0},0,{"$f":"D79*E79","v":0}]
[null,null,{"$f":"F!C86","v":"1 - 9 m"},{"$f":"F!D86","v":0},1,{"$f":"D80*E80","v":0}]
[null,null,{"$f":"F!C87","v":"10 - 29 m"},{"$f":"F!D87","v":0},2,{"$f":"D81*E81","v":0}]
[null,null,{"$f":"F!C88","v":"30 - 49 m"},{"$f":"F!D88","v":0},3,{"$f":"D82*E82","v":0}]
[null,null,{"$f":"F!C90","v":"> 100 m"},{"$f":"F!D90","v":0},4,{"$f":"D83*E83","v":0}]
[{"$f":"F!A95","v":"F18"},{"$f":"F!B95","v":"Interspersion of Robust Emergents & Open Water"},{"$f":"F!C95","v":"During most of the growing season, the spatial pattern of tall robust herbaceous vegetation (e.g., cattail, bulrush) that has surface water beneath it is mostly:"},null,null,null,{"$f":"IF((AllSat+AllSat>0),\"\",IF((NoPonded=1),\"\",IF((NoOpenPonded+NoOpenPonded1>0),\"\",IF((AllOpenPond=1),\"\", IF((SmallAA=1),\"\", MAX(F85:F87)/MAX(E85:E87))))))","v":0},"Interspers13","Interspersion of patches of open water amid patches of vegetation provides waterbirds with the best access to aquatic foods, and waterbird use of such wetlands has been shown to be significantly greater (Kaminski and Prince 1981, Murkin et al. 1982, Rehm & Baldassarre 2007, Schummer et al. 2012, Bolenbaugh et al. 2011).  In calculations, is excluded automatically (cell goes blank) if wetland never has surface water during an average year, if no ponded water, if ponded water but no vegetation, if ponded but no open water, or if <0.01 ha."]
[null,null,{"$f":"F!C96","v":"Scattered in small clumps, islands, or patches throughout the surface water area."},{"$f":"F!D96","v":0},3,{"$f":"D85*E85","v":0}]
[null,null,{"$f":"F!C97","v":"Intermediate"},{"$f":"F!D97","v":0},2,{"$f":"D86*E86","v":0}]
[null,null,{"$f":"F!C98","v":"Clumped at one or a few sides of the surface water area, or mostly surrounds a central area of open water.  Or such vegetation is absent or covers <9 sq m and <1% of the AA."},{"$f":"F!D98","v":0},1,{"$f":"D87*E87","v":0}]
[{"$f":"F!A99","v":"F19"},{"$f":"F!B99","v":"Isolated Island"},{"$f":"F!C99","v":"The AA contains (or is part of) an island or beaver lodge within a lake, pond, or river, and is isolated from the shore by water depths >2 m on all sides during an average June.  The island may be solid, or it may be a floating vegetation mat suitable for nesting waterbirds."},{"$f":"F!D99","v":0},null,null,{"$f":"IF((D88=0),\"\", IF((SmallAA=1),\"\", D88))","v":""},"Island13","Waterfowl nests on Islands that are inaccessible to mammalian predators are more successful (Loekmoen & Woodward 1992).  If wetland does not contain an island or is <0.01 ha, then ignored in calculations rather than being counted as a negative."]
[{"$f":"F!A101","v":"F21"},{"$f":"F!B101","v":"Stained Surface Water"},{"$f":"F!C101","v":"Most surface water is tea-colored (from tannins, not iron bacteria or silt), and/or its pH is usually <5.5. Nearby vegetation is mostly moss and/or conifers. "},{"$f":"F!D101","v":0},null,null,{"$f":"IF((AllSat+AllSat>0),\"\", IF((SmallAA=1),\"\", 1-D89))","v":1},"Acidic13","When non-acidic ponds are available, ducks prefer to nest in those rather than acidic lakes and wetlands (Epners et al. 2010).  Is excluded from calculations (cell goes blank) automatically if wetland is <0.01 ha."]
[{"$f":"F!A102","v":"F22"},{"$f":"F!B102","v":"Fish"},{"$f":"F!C102","v":"Fish (native or stocked) are known to be present in the AA.  Or fish can access at least part of the AA during one or more days annually.  If uncertain, use answer from Form OF, item  OF15, or enter \"0\"."},{"$f":"F!D102","v":0},null,null,{"$f":"IF((SmallAA=1),\"\", IF((D90=0),\"\", 1))","v":""},"Fish13","Fish are fed upon by several waterbird species, so their presence is considered generally beneficial.  However, one study found that breeding waterfowl density was twice as great in fishless lakes than in lakes with fish, after accounting for lake area, and some species occurred almost exclusively in fishless lakes (Epners et al. 2010).  If wetland lacks fish or is <0.01 ha, then ignored in calculations rather than being counted as a negative."]
[{"$f":"F!A103","v":"F23"},{"$f":"F!B103","v":"Beaver Probability"},{"$f":"F!C103","v":"Use of the AA by beaver during the past 5 years is (select most applicable ONE):"},null,null,null,{"$f":"IF((AllSat+AllSat>0),\"\",MAX(F92:F95)/MAX(E92:E95))","v":0},"Beaver13","At least in the short term, open water areas created by beaver dams provide excellent nesting and foraging habitat for several waterbird species (Hood & Bayley 2008, Bromley & Hood 2013).  In calculations, is excluded automatically (cell goes blank) if wetland never has surface water during an average year."]
[null,null,{"$f":"F!C104","v":"evident from direct observation or presence of gnawed limbs, dams, tracks, dens, lodges, or extensive stands of water-killed trees (snags)."},{"$f":"F!D104","v":0},5,{"$f":"D92*E92","v":0}]
[null,null,{"$f":"F!C105","v":"likely based on known occurrence in the region and proximity to suitable habitat, which may include: (a) a persistent freshwater wetland, pond, or lake, or a perennial low or mid-gradient (<10%) channel, and (b) a corridor or multiple stands of hardwood trees and shrubs in vegetated areas near surface water."},{"$f":"F!D105","v":0},2,{"$f":"D93*E93","v":0}]
[null,null,{"$f":"F!C106","v":"unlikely because site characteristics above are deficient, and/or this is a settled area or other area where beaver are routinely removed.  But beaver occur in this part of the region (i.e., within 25 km)."},{"$f":"F!D106","v":0},1,{"$f":"D94*E94","v":0}]
[null,null,{"$f":"F!C107","v":"none.  Beaver are absent from this part of the region."},{"$f":"F!D107","v":0},0,{"$f":"D95*E95","v":0}]
[{"$f":"F!A129","v":"F29"},{"$f":"F!B129","v":"Internal Gradient"},{"$f":"F!C129","v":"The gradient along most of the flow path within the AA is:"},null,null,null,{"$f":"MAX(F97:F100)/MAX(E97:E100)","v":0},"Gradient13","Most waterbirds favor ponded areas (that typically are flat) rather than flowing water that typifies slope wetlands."]
[null,null,{"$f":"F!C130","v":"<2%, or, no slope is ever apparent (i.e., flat). Or, the wetland is in a depression or pond with no inlet and no outlet."},{"$f":"F!D130","v":0},3,{"$f":"Steep13*E97","v":0}]
[null,null,{"$f":"F!C131","v":"2-5%"},{"$f":"F!D131","v":0},2,{"$f":"D98*E98","v":0}]
[null,null,{"$f":"F!C132","v":"6-10%"},{"$f":"F!D132","v":0},1,{"$f":"D99*E99","v":0}]
[null,null,{"$f":"F!C133","v":">10%"},{"$f":"F!D133","v":0},0,{"$f":"D100*E100","v":0}]
[{"$f":"F!A134","v":"F30"},{"$f":"F!B134","v":"Total Woody Cover -% of the Vegetated AA"},{"$f":"F!C134","v":"Within the entire vegetated part of the AA, the percentage occupied by trees or shrubs taller than 1 m is:"},null,null,null,{"$f":"MAX(F102:F106)/MAX(E102:E106)","v":0},"Woody13","Herbaceous rather than woody vegetation is the most attractive nesting cover for most species of waterbirds (Bolenbaugh et al. 2011), partly because it provides food as well as cover.  Trees near water edges discourage use of those areas by some waterbird species (Thomphson et al. 2012), probably because it potentially conceals or provides a perch for predators such as eagles and falcons (Shepherd & Lank 2004, Sprague et al. 2008). "]
[null,null,{"$f":"F!C135","v":"<5% of the vegetated AA, or there is no woody vegetation in the AA.  SKIP to F38 (N Fixers)"},{"$f":"F!D135","v":0},4,{"$f":"D102*E102","v":0}]
[null,null,{"$f":"F!C136","v":"5-25%.  "},{"$f":"F!D136","v":0},3,{"$f":"D103*E103","v":0}]
[null,null,{"$f":"F!C137","v":"25-50%"},{"$f":"F!D137","v":0},2,{"$f":"D104*E104","v":0}]
[null,null,{"$f":"F!C138","v":"50-75%"},{"$f":"F!D138","v":0},1,{"$f":"D105*E105","v":0}]
[null,null,{"$f":"F!C139","v":">75%"},{"$f":"F!D139","v":0},0,{"$f":"D106*E106","v":0}]
[{"$f":"F!A151","v":"F33"},{"$f":"F!B151","v":"Woody Diameter Classes"},{"$f":"F!C151","v":"Mark all the classes of woody plants within the AA, but only IF they comprise more than 5% of the woody canopy within the AA.  Do not count trees that adjoin but are not within the AA."},null,null,null,{"$f":"IF((NoTrees=1),\"\", (MAX(F108:F115)/MAX(E108:E115)))","v":0},"TreeForm13","Large-diameter trees are more important because of their potential to provide rookeries for herons and nest cavities for a few waterbird species, e.g., hooded merganser. Such trees may be used even when located a considerable distance from the wetland.  In calculations, is excluded automatically (cell goes blank) if trees occupy <5% of the vegetated part of the AA.  Otherwise, score is based on the  presence of the categories with the greatest weights, i.e., larger trees, which are more suitable as nest sites for herons, geese, and cavity-nesting ducks."]
[null,null,{"$f":"F!C152","v":"coniferous, 1-9 cm diameter and >1 m tall"},{"$f":"F!D152","v":0},0,{"$f":"D108*E108","v":0}]
[null,null,{"$f":"F!C153","v":"broad-leaved deciduous 1-9 cm diameter and >1 m tall"},{"$f":"F!D153","v":0},0,0]
[null,null,{"$f":"F!C154","v":"coniferous, 10-19 cm diameter"},{"$f":"F!D154","v":0},0,0]
[null,null,{"$f":"F!C155","v":"broad-leaved deciduous 10-19 cm diameter"},{"$f":"F!D155","v":0},0,0]
[null,null,{"$f":"F!C156","v":"coniferous, 20-40 cm diameter"},{"$f":"F!D156","v":0},2,0]
[null,null,{"$f":"F!C157","v":"broad-leaved deciduous 20-40 cm diameter"},{"$f":"F!D157","v":0},2,0]
[null,null,{"$f":"F!C158","v":"coniferous, >40 cm diameter"},{"$f":"F!D158","v":0},3,0]
[null,null,{"$f":"F!C159","v":"broad-leaved deciduous >40 cm diameter"},{"$f":"F!D159","v":0},3,0]
[{"$f":"F!A184","v":"F39"},{"$f":"F!B184","v":"Snags"},{"$f":"F!C184","v":"The number of large snags (diameter >20 cm) in the AA plus the upland area within 10 m of the wetland edge is:"},null,null,null,{"$f":"IF((NoTrees=1),\"\",MAX(F117:F119)/MAX(E117:E119))","v":0},"SnagB13","Snags provide nest cavities for a few waterbird species, e.g., hooded merganser. Such trees may be used even when located a considerable distance from the wetland."]
[null,null,{"$f":"F!C185","v":"Several ( >2/hectare) and a pond, lake, or slow-flowing water wider than 10 m is within 1 km."},{"$f":"F!D185","v":0},4,{"$f":"D117*E117","v":0}]
[null,null,{"$f":"F!C186","v":"Several ( >2/hectare) but above not true."},{"$f":"F!D186","v":0},1,{"$f":"D118*E118","v":0}]
[null,null,{"$f":"F!C187","v":"Few or none "},{"$f":"F!D187","v":0},0,{"$f":"D119*E119","v":0}]
[{"$f":"F!A213","v":"F45"},{"$f":"F!B213","v":"Shorebird Feeding Habitats"},{"$f":"F!C213","v":"During any 2 consecutive weeks of the growing season, the extent of mudflats, bare unshaded saturated areas not covered by thatch, and unshaded non-acidic waters shallower than 6 cm (see definition in column E) is:"},null,null,null,{"$f":"MAX(F121:F124)/MAX(E121:E124)","v":0},"SBhab13","Shorebirds are a large component of waterbird diversity.  Most shorebird species feed only on mudflats or in areas of short, sparse vegetation."]
[null,null,{"$f":"F!C214","v":"none, or <100 sq. m within the AA."},{"$f":"F!D214","v":0},0,{"$f":"D121*E121","v":0}]
[null,null,{"$f":"F!C215","v":"100-1000 sq. m within the AA."},{"$f":"F!D215","v":0},1,{"$f":"D122*E122","v":0}]
[null,null,{"$f":"F!C216","v":"1000 – 10,000 sq. m within the AA."},{"$f":"F!D216","v":0},2,{"$f":"D123*E123","v":0}]
[null,null,{"$f":"F!C217","v":">10,000 sq. m within the AA."},{"$f":"F!D217","v":0},3,{"$f":"D124*E124","v":0}]
[{"$f":"F!A218","v":"F46"},{"$f":"F!B218","v":"Herbaceous - Percent of Vegetated Wetland"},{"$f":"F!C218","v":"In aerial (\"ducks eye\") view, the maximum annual cover of dense herbaceous vegetation (graminoids + forbs, but not mosses and submerged and floating aquatics) is:"},null,null,null,{"$f":"MAX(F126:F130)/MAX(E126:E130)","v":0},"EmPct13","Most waterbirds favor emergent herbaceous vegetation rather than woody vegetation, partly because it provides food as well as cover. "]
[null,null,{"$f":"F!C219","v":"<5% of the vegetated part of the AA (excluding parts that are moss-covered or beneath shrubs or trees), or <0.01 hectare (whichever is less).  Mark \"1\" here and SKIP to F50 (Invasive Plant Cover)."},{"$f":"F!D219","v":0},0,{"$f":"D126*E126","v":0}]
[null,null,{"$f":"F!C220","v":"5-25% of the vegetated AA."},{"$f":"F!D220","v":0},2,{"$f":"D127*E127","v":0}]
[null,null,{"$f":"F!C221","v":"25-50% of the vegetated AA."},{"$f":"F!D221","v":0},3,{"$f":"D128*E128","v":0}]
[null,null,{"$f":"F!C222","v":"50-95% of the vegetated AA."},{"$f":"F!D222","v":0},4,{"$f":"D129*E129","v":0}]
[null,null,{"$f":"F!C223","v":">95% of the vegetated AA."},{"$f":"F!D223","v":0},5,{"$f":"D130*E130","v":0}]
[{"$f":"F!A249","v":"F52"},{"$f":"F!B249","v":"Natural Cover in Buffer"},{"$f":"F!C249","v":"Along the wetland-upland edge and extending 30 m upslope, the percentage of the upland that contains natural (not necessarily native -- see column E) land cover taller than 10 cm is:"},null,null,null,{"$f":"MAX(F132:F136)/MAX(E132:E136)","v":0},"BuffNatPct13","In herbaceous wetlands, the type of adjoining upland cover is very important to many nesting waterbird species (Horn et al. 2005, Bayley et al. 2013). Most upland-nesting waterfowl nest within about 1000 ft of wetlands. Maintaining mostly non-woody but natural vegetation in such areas makes it difficult for predators to find nests. "]
[null,null,{"$f":"F!C250","v":"<5% "},{"$f":"F!D254","v":0},0,{"$f":"D132*E132","v":0}]
[null,null,{"$f":"F!C251","v":"5 to 30%"},{"$f":"F!D253","v":0},2,{"$f":"D133*E133","v":0}]
[null,null,{"$f":"F!C252","v":"30 to 60%"},{"$f":"F!D252","v":0},3,{"$f":"D134*E134","v":0}]
[null,null,{"$f":"F!C253","v":"60 to 90%"},{"$f":"F!D251","v":0},4,{"$f":"D135*E135","v":0}]
[null,null,{"$f":"F!C254","v":">90%.  SKIP to F54 (Cliffs)."},{"$f":"F!D254","v":0},6,{"$f":"D136*E136","v":0}]
[{"$f":"F!A280","v":"F59"},{"$f":"F!B280","v":"Unvisited Core Area "},{"$f":"F!C280","v":"The percentage of the AA almost never visited by humans during an average growing season probably comprises: [Note: Do not include visitors on trails outside of the AA unless more than half the wetland is visible from the trails and they are within 30 m of the wetland edge.  In that case, imagine the percentage of the AA that would be covered by the trail if it were placed within the AA.]"},null,null,null,{"$f":"MAX(F138:F143)/MAX(E138:E143)","v":0},"Core1_13","Humans visiting wetlands commonly bring dogs, which potentially harass waterbirds.  Even the simple presence of people on foot will cause many waterbirds to take flight (Burger 1981; Klein et al. 1995; Burger & Gochfeld 1998).  Although some species may habituate to frequent disturbance more readily than others, repeated intrusions drain the energy of many waterbirds.  This is especially damaging during cold weather, or when birds (especially shorebirds) are stopping briefly to feed during long migrations."]
[null,null,{"$f":"F!C281","v":"<5% and no inhabited building is within 100 m of the AA"},{"$f":"F!D281","v":0},1,{"$f":"D138*E138","v":0}]
[null,null,{"$f":"F!C282","v":"<5% and inhabited building is within 100 m of the AA"},{"$f":"F!D282","v":0},0,0]
[null,null,{"$f":"F!C283","v":"5-50% and no inhabited building is within 100 m of the AA"},{"$f":"F!D283","v":0},3,0]
[null,null,{"$f":"F!C284","v":"5-50% and inhabited building is within 100 m of the AA"},{"$f":"F!D284","v":0},2,0]
[null,null,{"$f":"F!C285","v":"50-95%"},{"$f":"F!D285","v":0},4,0]
[null,null,{"$f":"F!C286","v":">95% of the AA"},{"$f":"F!D286","v":0},5,0]
[{"$f":"F!A287","v":"F60"},{"$f":"F!B287","v":"Frequently Visited Area"},{"$f":"F!C287","v":"The percentage of the AA visited by humans almost daily for several weeks during an average growing season probably comprises: [Note: Do not include visitors on trails outside of the AA unless more than half the wetland is visible from the trails and they are within 30 m of the wetland edge.   In that case, imagine the percentage of the AA that would be covered by the trail if it were placed within the AA.]"},null,null,null,{"$f":"MAX(F145:F148)/MAX(E145:E148)","v":0},"Core2_13","See above."]
[null,null,{"$f":"F!C288","v":"<5%.  If F59 was answered \">95%\", SKIP to F63 (Consumptive Uses)."},{"$f":"F!D288","v":0},3,{"$f":"D145*E145","v":0}]
[null,null,{"$f":"F!C289","v":"5-50%"},{"$f":"F!D289","v":0},2,{"$f":"D146*E146","v":0}]
[null,null,{"$f":"F!C290","v":"50-95%"},{"$f":"F!D290","v":0},1,{"$f":"D147*E147","v":0}]
[null,null,{"$f":"F!C291","v":">95% of the AA"},{"$f":"F!D291","v":0},0,{"$f":"D148*E148","v":0}]
[{"$f":"F!A293","v":"F62"},{"$f":"F!B293","v":"BMP - Wildlife Protection"},{"$f":"F!C293","v":"Fences, observation blinds, platforms, paved trails, exclusion periods, and/or well-enforced prohibitions on motorized boats, off-leash pets, and off road vehicles appear to effectively exclude or divert visitors and their pets from the AA at critical times in order to minimize disturbance of wildlife (except during hunting seasons).  Enter \"1\" if true. "},{"$f":"F!D293","v":0},null,null,{"$f":"IF((D143+D145>1),\"\",D149)","v":0},"BMP_13","Humans visiting wetlands commonly bring dogs, which potentially harass waterbirds, and human presence can attract crows and ravens, which prey on nests. Even the simple presence of people on foot and without dogs will cause many waterbirds to take flight. Repeated intrusions that drain the energy of waterbirds are especially damaging during the period when adult birds are searching for food to feed their young.  In calculations, is excluded automatically (cell goes blank) if last choice in F59 was chosen AND first choice in F60 was chosen."]
[{"$f":"F!A307","v":"F65"},{"$f":"F!B307","v":"Salinity, Alkalinity, Conductance "},{"$f":"F!C307","v":"Based on measurement from a surface water area larger than .01 hectare, the AA's surface water is mostly:"},null,null,null,{"$f":"IF((D154=1),\"\",IF((D151=1),0, \"\"))","v":""},"Salin13","Although some waterbirds (e.g., gadwall, phalaropes) use saline wetlands extensively, in general waterbird diversity tends to be less than in fresh or slightly brackish wetlands.  If wetland is saline or brackish the score for this indicator is 0.  Otherwise it is ignored."]
[null,null,{"$f":"F!C308","v":"Brackish or saline (conductance of >25 mS/cm, or >5000 ppm TDS). Or plants that indicate saline conditions comprise >20% of ground cover.  Trees and shrubs mostly absent.  Salt crust obvious around the perimeter and on flats."},{"$f":"F!D308","v":0},0,{"$f":"D151*E151","v":0}]
[null,null,{"$f":"F!C309","v":"Slightly brackish (conductance of 2.5- 25 mS/cm, or 500 - 5000 ppm TDS).  Or plants that indicate saline conditions comprise 1-20% of ground cover.  Salt crust may or may not be present along perimeter."},{"$f":"F!D309","v":0},1,{"$f":"D152*E152","v":0}]
[null,null,{"$f":"F!C310","v":"Fresh (conductance of < 2.5 mS/cm, or <500 ppm TDS). Plants that indicate saline conditions are sparse or absent. No salt crust along perimeter."},{"$f":"F!D310","v":0},1,{"$f":"D153*E153","v":0}]
[null,null,{"$f":"F!C311","v":"Unknown condition (was not measured because surface water absent or insufficient, or measurement conflicted with plant indicators). "},{"$f":"F!D311","v":0}]
[{"$f":"F!A328","v":"F69"},{"$f":"F!B328","v":"Plants or Animals of Conservation Concern"},{"$f":"F!C328","v":"If required, survey the AA for plant or animal species believed to be of conservation concern in Alberta (see list on Form F in Appendix A of Manual).  Do so at appropriate times of the year, especially if the data review conducted during the office phase of this assessment indicated their past presence in the general vicinity.  If you do detect these species or have reliable knowledge of their recent (within ~5 years) occurrence within the AA, indicate that below.  "},null,null,null,null,"RareWB13","Because of their relative rarity, these waterbird species contribute more to regional biodiversity than waterbird species with broader habitat tolerances."]
[null,null,{"$f":"F!C332","v":"One or more of the rare waterbird species was detected within the AA."},{"$f":"F!D332","v":0},null,null,{"$f":"IF((D156=0),\"\",1)","v":""}]
[]
[null,null,"Habitat Structure [HabStrucW]"]
[null,"Wetlands <10 hectares:","AVERAGE(WetVegArea,WatProb, ISOdry13, OWpct13, Interspers13, EmPct13, DepthEven13, SBhab13, ShoreSlope13, TreeForm13, SnagB13, Island13, VwidthAbs13)",null,null,null,{"$f":"IF((GT10HA=1),G160, IFERROR(AVERAGE(WetVegArea,WatProb, ISOdry13, OWpct13, Interspers13, EmPct13, DepthEven13, SBhab13, ShoreSlope13, TreeForm13, SnagB13, Island13, VwidthAbs13),\"\"))","v":0}]
[null,"Wetlands >10 hectares:","Substituted OWpct, MixWaterVeg",null,null,null,{"$f":"IFERROR(AVERAGE(WetVegArea,WatProb, ISOdry13, OWpct_WB, MixWaterVeg, EmPct13, DepthEven13, SBhab13, ShoreSlope13, TreeForm13, SnagB13,  Island13, VwidthAbs13),\"\")","v":0}]
[]
[null,null,"Habitat Productivity [CfixW]"]
[null,null,"AVERAGE(Gradient13, Wettype13, AVERAGE(GrowDD, RipFloodpl, Lake13, Fish13, SatPct13, Acidic13, Woody13, Beaver13,  Salin13, Fluctu13))",null,null,null,{"$f":"IFERROR(AVERAGE(Gradient13, Wettype13, AVERAGE(GrowDD, RipFloodpl, Lake13, Fish13, Acidic13, Woody13, Beaver13,  Salin13, SatPct13, Fluctu13)),\"\")","v":0.08}]
[]
[null,null,"Offsite Habitat Influence [LscapeW]"]
[null,null,"AVERAGE(WetDens1k, PerimNatCov, UndevOpenL1k, VegCon1k)",null,null,null,{"$f":"IFERROR(AVERAGE(WetDens1k, DuckDens, PerimNatCov, UndevOpenL1k, VegCon1k),\"\")","v":""}]
[]
[null,null,"Stressors (Lack of)  [StressW]"]
[null,null,"AVERAGE(Dist2DevCrop, BuffNatPct13, Core1_13, Core2_13, BMP_13)",null,null,null,{"$f":"IFERROR(AVERAGE(Dist2DevCrop, BuffNatPct13, Core1_13, Core2_13, BMP_13),\"\")","v":0}]
[]
[null,null,"ABWRET-A FUNCTION MODEL"]
[null,null,"Waterbird Habitat"]
[null,null,"IF((MAX(RareWB, IBirdArea, SwanArea, RareBirdUse, SBstaging, WBstaging)>0),10, ELSE: 10*AVERAGE(DuckDens, MarshPct, UniqFenMarsh, HabStrucW, CfixW, LscapeW, StressW))",null,null,null,{"$f":"IF((MAX(RareWB13,IBirdArea,TrumSwan, RareBirdUse, SBstaging, WBstaging)>0),10, 10*AVERAGE(DuckDens, MarshPct, UniqFenMarsh, HabStrucW1a, CfixW1a, LscapeW1a, StressW1a))","v":0.26666666666666666}]
[null,null,null,null,null,null,null,null,"Literature Cited"]
[null,null,"ABWRET-E model:",null,null,null,null,null,"Bolenbaugh, J. R., D. G. Krementz, and S. E. Lehnen. 2011. Secretive marsh bird species co-occurrences and habitat associations across the Midwest, USA. Journal of Fish and Wildlife Management 2:49-60."]
[null,1,"IF MAX(IBirdArea, RareBirdUse, TrumSwan, SBstaging, Wbstaging)>0, then =10",{"$f":"IFERROR(IF((MAX(IBirdArea, RareBirdUse, TrumSwan, SBstaging, WBstaging)>0), 10, \"\"),\"\")","v":""},null,null,null,null,"Arnold, T. W., L. M. Craig-Moore, L. M. Armstrong, D. W. Howerter, J. H. Devries, B. L. Joynt, R. B. Emery, and M. G. Anderson. 2007. Waterfowl use of dense nesting cover in the Canadian Parklands. Journal of Wildlife Management 71:2542-2549."]
[null,2,"ELSE calculate these averages:",null,null,null,null,null,"Baschuk, M. 2010. Effects of water-level management on the abundance and habitat use of waterfowl and marsh birds in the Saskatchewan River Delta, Manitoba, Canada. Master's Thesis. University of Manitoba, Manitoba, Canada."]
[null,"a","AVERAGE (WetVegArea, RipFloodpl) ",{"$f":"IFERROR(AVERAGE(WetVegArea, RipFloodpl),\"\")","v":""},null,null,null,null,"Baschuk, M. S., N. Koper, D. A. Wrubleski, and G. Goldsborough. 2012. Effects of water depth, cover and food resources on habitat use of marsh birds and waterfowl in boreal wetlands of Manitoba, Canada. Waterbirds 35:44-55."]
[null,"b","AVERAGE(MixWaterVeg, OWpct)",{"$f":"IFERROR(AVERAGE(MixWaterVeg, OWpct_WB),\"\")","v":""},null,null,null,null,"Bayley, S. E., A. S. Wong, and J. E. Thompson. 2013. Effects of agricultural encroachment and drought on wetlands and shallow lakes in the boreal transition zone of Canada. Wetlands 33:17-28."]
[null,"c","AVERAGE(WetDens1k_OW, DuckDens)",{"$f":"IFERROR(AVERAGE(WetDens1k_OW, DuckDens),\"\")","v":""},null,null,null,null,"Bloom, P. M., R. G. Clark, D. W. Howerter, and L. M. Armstrong. 2012. Landscape-level correlates of mallard duckling survival: Implications for conservation programs. Journal of Wildlife Management 76:813-823.\n"]
[null,"d","AVERAGE(Dist2DevCrop, PerimNatCov, UndevOpenL1k, VegCon1k)",{"$f":"IFERROR(AVERAGE(Dist2DevCrop, PerimNatCov, UndevOpenL1k, VegCon1k),\"\")","v":""},null,null,null,null,"Bromley, C. K. and G.A. Hood. 2013. Beavers (Castor canadensis) facilitate early access by Canada geese (Branta canadensis) to nesting habitat and areas of open water in Canada's boreal wetlands. Mammalian Biology 78(1):73-77."]
[null,3,"10*AVERAGE(MarshPct, UniqFenMarsh, a, b, c, d)",{"$f":"IFERROR(IF((D176=10),10, 10*AVERAGE(MarshPct, UniqFenMarsh,D178:D181)),\"\")","v":""},null,null,null,null,"Burger, J. 1981. The effect of human activity on birds at a coastal bay. Biological Conservation 21:231-241."]
[null,null,null,null,null,null,null,null,"Burger, J. and M. Gochfeld. 1991. Human activity influence and diurnal and nocturnal foraging of sanderlings (Calidris alba). Condor 93:259-265."]
[null,null,"ABWRET-E with substitutions:",null,null,null,null,null,"Devries, J. H. and L. M. Armstrong. 2011. Impact of management treatments on waterfowl use of dense nesting cover in the Canadian Parklands. Journal of Wildlife Management 75:1340-1349."]
[null,1,"IF MAX(IBArea, RareBirdUse, SwanArea, SBstaging, WBstaging) >0, then =10",{"$f":"IFERROR(IF((MAX(IBirdArea, RareBirdUse, TrumSwan, SBstaging, WBstaging)>0), 10, \"\"),\"\")","v":""},null,null,null,null,"Epners, C. A., S. E. Bayley, J. E. Thompson, and W. M. Tonn. 2010. Influence of fish assemblage and shallow lake productivity on waterfowl communities in the Boreal Transition Zone of western Canada. Freshwater Biology 55:2265-2280."]
[null,2,"ELSE calculate these averages:",null,null,null,null,null,"Forcey, G. M., W. E. Thogmartin, G. M. Linz, W. J. Bleier, and P. C. McKann. 2011. Land use and climate influences on waterbirds in the Prairie Potholes. Journal of Biogeography 38:1694-1707."]
[null,"a","AVERAGE (WetVegArea, RipFloodpl) ",{"$f":"IFERROR(AVERAGE(WetVegArea, RipFloodpl),\"\")","v":""},null,null,null,null,"Hood, G. A. and S. E. Bayley. 2008. Beaver (Castor canadensis) mitigate the effects of climate on the area of open water in boreal wetlands in western Canada. Biological Conservation 141:556-567."]
[null,"b","AVERAGE(Interspers13, OWpct13)",{"$f":"IFERROR(AVERAGE(Interspers13, OWpct13),\"\")","v":0},null,null,null,null,"Horn, D. J., M. L. Phillips, R. R. Koford, W. R. Clark, M. A. Sovada, and R. J. Greenwood. 2005. Landscape composition, patch size, and distance to edges: Interactions affecting duck reproductive success. Ecological Applications 15:1367-1376."]
[null,"c","AVERAGE(WetDens1k_OW, DuckDens)",{"$f":"IFERROR(AVERAGE(WetDens1k_OW, DuckDens),\"\")","v":""},null,null,null,null,"Kaminski, R. M. and H. H. Prince. 1981. Dabbling duck and aquatic macro-invertebrate responses to manipulated wetland habitat. Journal of Wildlife Management 45:1–15."]
[null,"d","AVERAGE(DistDevCrop, PerimNatCov, UndevOpenL1k, VegCon1k)",{"$f":"IFERROR(AVERAGE(Dist2DevCrop, PerimNatCov, UndevOpenL1k, VegCon1k),\"\")","v":""},null,null,null,null,"Klein, M. L., S. R. Humphrey, and H. F. Percival. 1995. Effects of ecotourism on distribution of waterbirds in a wildlife refuge. Conservation Biology 9:1454-1465."]
[null,3,"10*AVERAGE(MarshPct, UniqFenMarsh, a, b, c, d)",{"$f":"IF((D185=10),10, 10*AVERAGE(MarshPct, UniqFenMarsh,D187:D190))","v":0},null,null,null,null,"Lokemoen, J. T. and R. O. Woodward. 1992. Nesting waterfowl and water birds on natural islands in the Dakotas and Montana. Wildlife Society Bulletin 20:163-171."]
[null,null,null,null,null,null,null,null,"Murkin, H. R., R. M. Kaminski, and R. D. Titman. 1982. Responses by dabbling ducks and aquatic invertebrates to an experimentally manipulated cattail marsh. Canadian Journal of Zoology 60:2324-2332."]
[null,null,null,null,null,null,null,null,"Naugle, D. E., K. F. Higgins, M. E. Estey, R. R. Johnson, and S. M. Nusser. 2000. Local and landscape-level factors influencing black tern habitat suitability. Journal of Wildlife Management 64:253-260."]
[null,null,null,null,null,null,null,null,"Rehm, E. M. and G. A. Baldassarre. 2007. The influence of interspersion on marsh bird abundance in New York. Wilson Journal of Ornithology 119:648-654."]
[null,null,null,null,null,null,null,null,"Shepherd, P. C. F. and D. B. Lank. 2004. Marine and agricultural habitat preferences of dunlin wintering in British Columbia. Journal of Wildlife Management 68:61-73."]
[null,null,null,null,null,null,null,null,"Sprague, A. J., D. J. Hamilton, and A. W. Diamond. 2008. Site safety and food affect movements of Semipalmated Sandpipers (Calidris pusilla) migrating through the upper Bay of Fundy. Avian Conservation and Ecology 3:1-22."]
[null,null,null,null,null,null,null,null,"Silver, C. A., J. E. Thompson, A. S. Wong, and S. E. Bayley. 2012. Relationship between wetland macroinvertebrates and waterfowl along an agricultural gradient in boreal transition zone of western Canada. Northwestern Naturalist 93:40-59.\n"]
[null,null,null,null,null,null,null,null,"Thompson, S. J., T. W. Arnold, and S. Vacek. 2012. Impact of encroaching woody vegetation on nest success of upland nesting waterfowl. Journal of Wildlife Management 76:1635-1642."]

{"sheet":"SBM","index":20,"n_rows":246,"n_cols":9,"rows_kept":246,"cut":false,"hidden":false,"merged":[[113,0,118,0],[133,0,137,0],[113,1,118,1],[39,0,45,0],[81,0,85,0],[147,0,149,0],[141,1,146,1],[104,0,109,0],[151,8,157,8],[70,1,74,1],[141,0,146,0],[70,8,74,8],[133,8,137,8],[86,1,91,1],[81,1,85,1],[119,0,122,0],[104,1,109,1],[92,1,100,1],[141,8,146,8],[147,8,149,8],[151,0,157,0],[39,8,45,8],[46,8,52,8],[86,0,91,0],[119,8,122,8],[158,1,162,1],[113,8,118,8],[123,8,126,8],[151,1,157,1],[127,8,132,8],[127,1,132,1],[81,8,85,8],[101,8,103,8],[133,1,137,1],[101,1,103,1],[138,8,140,8],[158,8,162,8],[119,1,122,1],[119,7,122,7],[123,1,126,1],[138,1,140,1],[110,8,112,8],[104,7,109,7],[110,7,112,7],[113,7,118,7],[147,7,149,7],[110,1,112,1],[110,0,112,0],[101,0,103,0],[92,0,100,0],[66,8,69,8],[66,0,69,0],[39,1,45,1],[28,0,32,0],[70,0,74,0],[33,1,38,1],[33,7,38,7],[60,1,65,1],[46,0,52,0],[60,0,65,0],[53,0,59,0],[66,1,69,1],[33,8,38,8],[101,7,103,7],[86,7,91,7],[92,7,100,7],[46,1,52,1],[28,8,32,8],[28,1,32,1],[53,1,59,1],[104,8,109,8],[53,8,59,8],[75,1,80,1],[75,0,80,0],[75,8,80,8],[53,7,59,7],[60,7,65,7],[81,7,85,7],[66,7,69,7],[70,7,74,7],[75,7,80,7],[0,4,0,8],[164,1,165,1],[164,8,165,8],[164,0,165,0],[123,7,126,7],[127,7,132,7],[133,7,137,7],[138,7,140,7],[141,7,146,7],[147,1,149,1],[158,0,162,0],[127,0,132,0],[138,0,140,0],[123,0,126,0],[151,7,157,7],[158,7,162,7],[33,0,38,0],[28,7,32,7],[39,7,45,7],[46,7,52,7],[0,0,0,1],[60,8,65,8],[92,8,100,8],[86,8,91,8]]}
["Songbird,          Raptor, &          Mammal                       Habitat",null,"The capacity to support or contribute to an abundance or diversity of native songbird, raptor, and mammal species and functional groups, especially those that are most dependent on wetlands or water.","SBM"]
["#","Function Indicators from Estimator","Scoring Notes",null,null,null,"Normalised Score","Indicator Abbreviation or Formula","Rationale"]
[{"$f":"OF!A4","v":"OF3"},{"$f":"OF!C4","v":"Key Wildlife Biodiversity Zone"},"If not within Key Wildlife Biodiversity Zone then this indicator is ignored (NULL) in calculations.",null,null,null,{"$f":"IF((BioDivZone=\"\"),\"\",IF((BioDivZone=1),1,\"\"))","v":""},"BioDivZone","This spatial data layer mainly indicates areas of relatively intact habitat along major river corridors and valley slope breaks. The data correlate with ungulate winter densities but likely indicate high suitability for many valued songbirds and raptors as well."]
[{"$f":"OF!A6","v":"OF5"},{"$f":"OF!C6","v":"Wetland Class Richness Within 1km"}," ",null,null,null,{"$f":"IF((ClassRich1k=\"\"),\"\",ClassRich1k)","v":""},"ClassRich1k","To some degree, different bird and mammal species associate with different wetland classes.  Thus, greater class richness supports greater richness of these groups."]
[{"$f":"OF!A7","v":"OF6"},{"$f":"OF!C7","v":"Wetland Class Richness Within Wetland"}," ",null,null,null,{"$f":"IF((ClassRichIn=\"\"),\"\",ClassRichIn)","v":""},"ClassRichIn","See above"]
[{"$f":"OF!A8","v":"OF7"},{"$f":"OF!C8","v":"Distance to Nearest Annual Cropland or Developed Land"}," ",null,null,null,{"$f":"IF((Dist2DevCrop=\"\"),\"\",Dist2DevCrop)","v":""},"Dist2DevCrop","Chemicals and house cats that can harm wetland birds and mammals are most prevalent where wetlands or their tributaries are adjoined by agricultural or developed lands."]
[{"$f":"OF!A9","v":"OF8"},{"$f":"OF!C9","v":"Distance to Nearest Road (from Wetland Edge)"}," ",null,null,null,{"$f":"IF((Dist2Road=\"\"),\"\",Dist2Road)","v":""},"Dist2Road","Traffic poses a hazard to songbirds and mammals that attempt to cross roads (Forman et al. 2002, Clevenger et al. 2003, Massey et al. 2008, Minor & Urban 2010, Tremblay & St. Clair 2010, and see reviews by Fahrig & Rytwinski 2009, Benitez-Lopez et al. 2010). Roadsides also may channel the movements of predators. Noise from heavy traffic interferes with bird reproduction because some birds cannot hear singing of prospective mates (Wood & Yezerinac 2006, Slabbekoorn & Ripmeester 2008, Barber et al. 2010) and road noise can restrict habitat use by bats (Schaub et al. 2008). Grizzly bears avoid habitat within 0.5 km from highways; Waller and Servheen 2005, McLellen and Shackleton 1988). In a study examining the spatial patterns and factors influencing small terrestrial vertebrate road-kill aggregations in the Bow River Valley of Alberta, Canada, mammal and bird road-kill indices were consistently higher on low volume parkway roads than on the high-speed, high volume highways (Clevenger et al. 2003).    "]
[{"$f":"OF!A10","v":"OF9"},{"$f":"OF!C10","v":"Distance to Nearest Well-settled Area"}," ",null,null,null,{"$f":"IF((DistPop=\"\"),\"\",DistPop)","v":""},"DistPop","High nest predation occurs on the edges of residential areas because jays and ravens are more abundant there (Saab 1999), as well as in clearcut openings, edges, and interior forest, where squirrels are a common nest predator [Desanto & Wilson 2001]. Human settlements are accompanied by an increase in refuse, whether it be illegally dumped trash, recklessly contained household garbage, or well-intended compost piles. These serve as a food for ravens that prey extensively on native songbirds, frogs, and other wildlife (Chace & Walsh 2006). Populations of predatory crows and ravens have been shown to increase up to at least 0.5 mile from new urban areas (Oneal & Rotenberry 2009). "]
[{"$f":"OF!A18","v":"OF17"},{"$f":"OF!C18","v":"Growing Degree Days"}," ",null,null,null,{"$f":"IF((GrowDD=\"\"),\"\",GrowDD)","v":""},"GrowDD","Compared to other type of variables, climate factors are, in aggregate, the most important determinants of bird species richness across all of Boreal Canada (Hawkins et al. 2003). "]
[{"$f":"OF!A27","v":"OF26"},{"$f":"OF!C27","v":"Interspersion Index for Internal Herbaceous & Woody Vegetation (macroscale)"}," ",null,null,null,{"$f":"IF((MixHerbWood=\"\"),\"\",MixHerbWood)","v":""},"MixHerbWood","Gaps in woody canopy, or scattered trees and shrubs within a marsh or bog, together provide both food and cover and thus support a wider variety of birds and mammals.  These conditions also sometimes indicate a diversity of underlying hydroperiods that have the same effect."]
[{"$f":"OF!A28","v":"OF27"},{"$f":"OF!C28","v":"Interspersion Index for Internal Water & Vegetation (macroscale)"}," ",null,null,null,{"$f":"IF((MixWaterVeg=\"\"),\"\",MixWaterVeg)","v":""},"MixWaterVeg","Greater bird diversity in wetlands is strongly associated with a well-mixed pattern of water and vegetation, e.g., the \"hemi-marsh\". This provides  food and cover in close proximity."]
[{"$f":"OF!A29","v":"OF28"},{"$f":"OF!C29","v":"% Natural Cover within 1km"}," ",null,null,null,{"$f":"IF((NatCov1k=\"\"),\"\",NatCov1k)","v":""},"NatCov1k","The total proportion of the land that is natural land cover, as well as its proximity, can affect songbird and mammal richness in wetlands. In Ohio, migrant songbirds had the strongest positive correlation with natural land cover near streams when it was measured within ~820 ft of streams, rather than in areas closer or farther. Some migrant songbirds were much less likely to occur where there were many buildings within that distance of streams (Pennington 2008). However, one study found that migrant bird abundance was statistically unrelated to either percent urbanized land or percent forest cover within 0.6 mile (Rodewald & Mathews 2005).  High nest predation was found in clearcut openings and edges where squirrels were a common nest predator throughout. [Desanto & Wilson 2001]. Younger forests that develop after clearcutting often contain mixed alder-conifer stands which provide significantly higher understory biomass than in pure conifer forests. Many songbirds and mammals occur only in larger tracts of natural land cover. Fragmentation of wooded riparian areas by residential development or clearcuts can, over the long term, reduce the diversity of songbirds nesting in the remaining patches (e.g., Smith & Wachob 2006). Breeding wetland birds sometimes do persist in small disturbed wetlands as long as much larger undisturbed wetlands nearby remain productive (e.g., Vermaat et al. 2008). Ideally, no clearing should result in a forest being fragmented into an isolate smaller than about 100 acres or narrower than 150 feet, and definitely not smaller than 2 acres or narrower than 100 feet (Donnelly & Marzluff 2004).Theoretical and limited empirical data suggest that 30% or more forest cover across a large area is the threshold value above which landscapes might provide sufficient habitat and connectivity for many forest species, allowing those species' populations to survive even in small remaining patches (Andren 1994). Minimum patch sizes required for breeding by those forest songbirds (e.g., brown Creeper) which may be the most sensitive to forest fragmentation in the Pacific Northwest may be about 25 acres (Donnelly & Marzluff 2004, Poulin et al. 2008). However, a study in British Columbia found patch size had little to do with the abundance or diversity of birds in patches of old growth forest (Schieck et al. 1995)."]
[{"$f":"OF!A31","v":"OF30"},{"$f":"OF!C31","v":"% of AA that is Open Water (macro scale)"},"Inverse",null,null,null,{"$f":"IF((OWpct=\"\"),\"\",1-OWpct)","v":""},"OWpct","A large proportion of open water in a wetland implies less emergent vegetation is present to provide cover, food, and perches for songbirds, raptors, and mammals, so the scoring is inverse.  "]
[{"$f":"OF!A35","v":"OF34"},{"$f":"OF!C35","v":"% of Wetland Perimeter Adjoined by Natural Cover"}," ",null,null,null,{"$f":"IF((PerimNatCov=\"\"),\"\",PerimNatCov)","v":""},"PerimNatCov","During summer months, grizzly bears select habitat in southern Alberta that is near wetlands, lakes, and ponds (Chetkiewicz & Boyce (2009). Many other wetland-dependent birds and mammals select wetlands that are close to other wetlands, to which their offspring can more readily disperse with less risk of being preyed upon."]
[{"$f":"OF!A38","v":"OF37"},{"$f":"OF!C38","v":"Sensitive Raptor Nesting Area"}," If wetland not within Sensitive Raptor Nesting Area then ignored (NULL) in calculations.",null,null,null,{"$f":"IF((RaptorNest=\"\"),\"\",IF((RaptorNest=1),1, \"\"))","v":""},"RaptorNest","Wetlands are important to several Alberta raptor species. Although survey data are not comprehensive and current, known occurrences of nesting raptors should elevate a wetland's score for this function."]
[{"$f":"OF!A41","v":"OF40"},{"$f":"OF!C41","v":"Road Density in 1km Buffer"},"Inverse",null,null,null,{"$f":"IF((RdDens1k=\"\"),\"\",1-RdDens1k)","v":""},"RdDens1k","See OF8 above."]
[{"$f":"OF!A43","v":"OF42"},{"$f":"OF!C43","v":"Riparian or Floodway Location"},"If wetland not within riparian or floodplain area then ignored (NULL) in calculations.",null,null,null,{"$f":"IF((RipFloodpl=\"\"),\"\",IF((RipFloodpl=1),1,\"\"))","v":""},"RipFloodpl","Riparian areas are often favoured as travel corridors by songbirds and wetland mammals."]
[{"$f":"OF!A51","v":"OF50"},{"$f":"OF!C51","v":"Springs within 300m"},"If wetland lacks a spring then ignored (NULL) in calculations.",null,null,null,{"$f":"IF((Spring=\"\"),\"\",IF((Spring=1),1,\"\"))","v":""},"Spring","Springs are important to several wetland songbird and mammal species. Although springs have not been surveyed comprehensively, known locations should elevate a wetland's score for this function."]
[{"$f":"OF!A57","v":"OF56"},{"$f":"OF!C57","v":"Local Uniqueness of Wetland's Class"}," ",null,null,null,{"$f":"IF((UniqClass=\"\"),\"\",UniqClass)","v":""},"UniqClass","If a particular class is significantly present in a wetland but scarce in the surrounding area, the contribution of wildlife species (that associate with that class) to local biodiversity is likely to be greater."]
[{"$f":"OF!A60","v":"OF59"},{"$f":"OF!C60","v":"Vegetation Connectivity to Other Wetlands within 1 km"}," ",null,null,null,{"$f":"IF((VegCon1k=\"\"),\"\",VegCon1k)","v":""},"VegCon1k","Wetlands that are closer to natural land cover and not separated by roads that interfere with movements across the landscape, are more likely to support a large diversity of songbird and mammal species. Forest gaps deter red squirrel movement (Bakker & Van Vuren 2004) and hinder movements of many birds. Nests in wetland forest edges, where both jays and squirrels occur frequently, were found to be depredated more often than those in wetland openings or forest interior, where predators were less common (Desanto & Wilson 2001).  The type as well as the amount of upland cover near the wetland is important to mammals and nesting songbirds. For most species, impervious surfaces are unusable. Habitat gaps caused by placement of roads, driveways, or homes – as well as by natural features such as rockslides and wide channels -- can impact movements of mammals and birds (Trombulak & Frissell 2000, Ortega & Capen 2002). This is especially true when the gaps are wider than about 100 feet (Rich et al. 1994, Rail et al. 1997, St. Clair et al. 1998, Belisle & Desrochers 2002, Laurance et al. 2004, Tremblay & St. Clair 2010), and definitely when wider than 200 ft (Creegan & Osborne 2005, Bosschieter & Goedhart 2005, Awade & Metzger 2008, Lees & Peres 2009). Species that prefer low vegetation may be particularly reluctant to cross forest clearings. The presence of small clusters of trees scattered within very wide forest gaps may be sufficient to enhance willingness of some forest bird species to cross those gaps (Robertson & Radford 2009). "]
[{"$f":"OF!A61","v":"OF60"},{"$f":"OF!C61","v":"Water Permanence Probability"},"Inverse",null,null,null,{"$f":"IF((WatProb=\"\"),\"\",1-WatProb)","v":""},"WatProb","A high probability of there being permanent surface water in a wetland implies vegetation cover is likely to be less extensive (due to soil anoxia), and that vegetation would otherwise provides cover, food, and perches for songbirds, raptors, and mammals.  Thus the scoring is inverse.  "]
[{"$f":"OF!A64","v":"OF63"},{"$f":"OF!C64","v":"Wetland Density Within 1km"}," ",null,null,null,{"$f":"IF((WetDens1k=\"\"),\"\",WetDens1k)","v":""},"WetDens1k","A wetland-dependent Alberta bird -- common yellowthroat -- occurs most frequently when >20% of the land cover within 1 km contains suitable wetlands, and a bird species that uses wooded wetlands regularly -- American redstart -- occurs most frequently when >30% of the land cover within 2 km contains suitable habitat (Betts et al. 2007).  "]
[{"$f":"OF!A68","v":"OF67"},{"$f":"OF!C68","v":"Perimeter-Area Ratio"}," ",null,null,null,{"$f":"IF((WetPerim2Area=\"\"),\"\",WetPerim2Area)","v":""},"WetPerim2Area","Wetlands with a large perimeter-to-area ratio (i.e., convoluted edges) or upland inclusions allow animals to move more conveniently between uplands and wetlands, using resources in each. In particular, small mammals avoid wetter (usually more central) parts of wetlands in favor of drier edges (Mazerolle et al. 2001).  In British Columbia, activity levels of bats were more than 40 times greater in riparian than in upland areas, due to greater abundance of emerging aquatic insects, and were significantly greater where stand complexity and extent of forest edges was greater; bat activity levels were not correlated with forest stand age (Grindal et al. Brigham 1999, Grindal et al. 1999)."]
[{"$f":"OF!A69","v":"OF68"},{"$f":"OF!C69","v":"Wetland Vegetated Area"}," ",null,null,null,{"$f":"IF((WetVegArea=\"\"),\"\",WetVegArea)","v":""},"WetVegArea","Larger wetlands are used disproportionately by some species of nesting wetland-dependent songbirds. Smaller identical wetlands of equal cumulative area probably support lower numbers and cumulative richness of songbirds and mammals, unless they are close together and connected with corridors of undeveloped land.  However, for predicting bird diversity, some evidence from peatlands (Calmer and Desrochers 2000) suggests that wetland size may be less important than microhabitat heterogeneity (which is represented by other  indicators). "]
[{"$f":"OF!A70","v":"OF69"},{"$f":"OF!C70","v":"% of Wetland Classified as Swamp or Forested (macro scale)"}," ",null,null,null,{"$f":"IF((WetWooded=\"\"),\"\",WetWooded)","v":""},"WetWooded","Trees add structure  "]
[{"$f":"OF!A72","v":"OF71"},{"$f":"OF!C72","v":"Wind Energy - Winter "},"Inverse",null,null,null,{"$f":"IF((WindWin=\"\"),\"\",1-WindWin)","v":""},"WindWin","Wind is a major physiologic stress for wintering songbirds."]
[{"$f":"OF!A73","v":"OF72"},{"$f":"OF!C73","v":"Surface Water Quality Risk Index"},"Inverse",null,null,null,{"$f":"IF((WQrisk=\"\"),\"\",1-WQrisk)","v":""},"WQrisk","Some chemicals that accumulate in food chains can harm wetland raptors and other species.  Chemicals are most prevalent where wetlands or their tributaries are adjoined by agricultural or developed lands."]
["#","Function Indicators from Onsite Visit","Categorical Choices","Data","Weight","Data  x  Weight","Normalised Score","Indicator Abbreviation or Formula","Rationale & Scoring Notes"]
[{"$f":"F!A6","v":"F1"},{"$f":"F!B6","v":"Wetland Type - Predominant"},{"$f":"F!C6","v":"Most of the vegetated part of the AA (wetland Assessment Area) is a (select ONE):"},null,null,null,{"$f":"IF((D31+NoOtherWettypes=2),0,\"\")","v":""},"Wettype14","Species richness of songbirds and mammals tends to be lower in bogs than in other wetland classes. In the calculations, If bog is the only class present the score is set to 0.  Otherwise this indicator is excluded (set to blank)."]
[null,null,{"$f":"F!C7","v":"Wooded Swamp"},{"$f":"F!D7","v":0}]
[null,null,{"$f":"F!C8","v":"Bog"},{"$f":"F!D8","v":0}]
[null,null,{"$f":"F!C9","v":"Fen"},{"$f":"F!D9","v":0}]
[null,null,{"$f":"F!C10","v":"Marsh or Shallow Open Water"},{"$f":"F!D10","v":0}]
[{"$f":"F!A11","v":"F2"},{"$f":"F!B11","v":"Wetland Types - Subordinate"},{"$f":"F!C11","v":"Mark all other vegetated wetland types in the AA that occupy more than 1 hectare or more than 1% of the vegetated AA.  Do not mark the predominant type again.  If AA is larger than 1 ha, see preliminary imagery-based answer provided by AESRD, but field-verify."},null,null,null,{"$f":"IF((D39=1),\"\",(1+SUM(D35:D38))/4)","v":0.25},"ClassRichIn14","The number of bird and mammal species using a wetland is greater if more wetland classes are present within the wetland. The score is the number of classes (including one from above) divided by 4."]
[null,null,{"$f":"F!C12","v":"Wooded Swamp"},{"$f":"F!D12","v":0}]
[null,null,{"$f":"F!C13","v":"Bog"},{"$f":"F!D13","v":0}]
[null,null,{"$f":"F!C14","v":"Fen"},{"$f":"F!D14","v":0}]
[null,null,{"$f":"F!C15","v":"Marsh or Shallow Open Water"},{"$f":"F!D15","v":0}]
[null,null,{"$f":"F!C16","v":"no types other than the predominant one in F1 meet the area threshold."},{"$f":"F!D16","v":0}]
[{"$f":"F!A17","v":"F3"},{"$f":"F!B17","v":"% Saturated Only"},{"$f":"F!C17","v":"The percentage of the AA that never contains surface water during an average year (that is, except perhaps for a few hours after snowmelt or rainstorms), but which is still a wetland, is:"},null,null,null,{"$f":"MAX(F41:F46)/MAX(E41:E46)","v":0},"SatPct14","Most songbirds prefer to nest in drier parts of wetlands because ground cover and vegetation height, which provide essential structure, tend to be greater there."]
[null,null,{"$f":"F!C18","v":"less than 1%, or <0.01 hectare (about 10 m on a side) never has surface water.  In other words, all or nearly all of the AA is inundated permanently or at least seasonally."},{"$f":"F!D18","v":0},1,{"$f":"D41*E41","v":0}]
[null,null,{"$f":"F!C19","v":"1-25% of the AA never contains surface water."},{"$f":"F!D19","v":0},2,0]
[null,null,{"$f":"F!C20","v":"25-50% of the AA never contains surface water."},{"$f":"F!D20","v":0},3,0]
[null,null,{"$f":"F!C21","v":"50-99% of the AA never contains surface water."},{"$f":"F!D21","v":0},4,0]
[null,null,{"$f":"F!C22","v":">99% of the AA never contains surface water, except for water flowing in channels and/or in pools that occupy <1% of the AA. SKIP to F26 (Channel Connection & Outflow Duration)"},{"$f":"F!D22","v":0},6,0]
[null,null,{"$f":"F!C23","v":">99% of the AA never contains surface water, and AA is not intersected by channels that have flow, not even for a few days per year. SKIP to F26."},{"$f":"F!D23","v":0},5,0]
[{"$f":"F!A24","v":"F4"},{"$f":"F!B24","v":"% with Persistent Surface Water"},{"$f":"F!C24","v":"The percentage of the AA that has surface water (either ponded or flowing, either open or obscured by vegetation) during all of the growing season during most years is:"},null,null,null,{"$f":"IF((AllSat+AllSat>0),\"\", MAX(F48:F53)/MAX(E48:E53))","v":0},"PermWpct14","Parts of wetlands that remain flooded most of the time will support fewer small mammals and songbirds. Wetlands with at least a little persistent water are important to aerially-foraging swallows, swifts, and flycatchers, as well as bats, muskrat, beaver, moose, and many other mammals. In calculations, is excluded automatically (cell goes blank) if wetland never has surface water during an average year. "]
[null,null,{"$f":"F!C25","v":"less than 1%, or <0.01 hectare (whichever is less).  SKIP to F8 (% Flooded Only Seasonally)."},{"$f":"F!D25","v":0},5,{"$f":"D48*E48","v":0}]
[null,null,{"$f":"F!C26","v":"1-25% of the AA, and mostly in narrow channels and/or small scattered pools."},{"$f":"F!D26","v":0},4,0]
[null,null,{"$f":"F!C27","v":"1-25% of the AA, and mostly in a single large pool, pond, and/or channel."},{"$f":"F!D27","v":0},4,0]
[null,null,{"$f":"F!C28","v":"25-50% of the AA"},{"$f":"F!D28","v":0},3,0]
[null,null,{"$f":"F!C29","v":"50-95% of the AA"},{"$f":"F!D29","v":0},2,0]
[null,null,{"$f":"F!C30","v":">95% of the AA"},{"$f":"F!D30","v":0},0,0]
[{"$f":"F!A71","v":"F14"},{"$f":"F!B71","v":"% of Ponded Water That Is Open "},{"$f":"F!C71","v":"In ducks-eye aerial view, the percentage of the ponded water that is open (lacking emergent vegetation during most of the growing season, and unhidden by a forest or shrub canopy) is:"},null,null,null,{"$f":"IF((AllSat+AllSat>0),\"\", IF((SmallAA=1),\"\", MAX(F55:F60)/MAX(E55:E60)))","v":0},"PondedOWpct14","Open water lacks vertical structure and thus supports fewer songbird species than land, so a large proportion of open water in a wetland implies lower overall songbird richness. In calculations, is excluded automatically (cell goes blank) if wetland never has surface water during an average year.  Also is excluded automatically if wetland has no ponded water or is <0.01 ha.."]
[null,null,{"$f":"F!C72","v":"<1% or none, or largest pool occupies <0.01 hectares.  Enter \"1\" and SKIP to F20 (Floating Algae & Duckweed)."},{"$f":"F!D72","v":0},4,{"$f":"D55*E55","v":0}]
[null,null,{"$f":"F!C73","v":"1-5% of the ponded water.  Enter \"1\" and SKIP to F20."},{"$f":"F!D73","v":0},5,0]
[null,null,{"$f":"F!C74","v":"5-30% of the ponded water."},{"$f":"F!D74","v":0},3,0]
[null,null,{"$f":"F!C75","v":"30-70% of the ponded water."},{"$f":"F!D75","v":0},2,0]
[null,null,{"$f":"F!C76","v":"70-99% of the ponded water."},{"$f":"F!D76","v":0},1,0]
[null,null,{"$f":"F!C77","v":"100% of the ponded water. "},{"$f":"F!D77","v":0},0,0]
[{"$f":"F!A84","v":"F16"},{"$f":"F!B84","v":"Predominant Width of Vegetated Zone within Wetland"},{"$f":"F!C84","v":"At the driest time of year (or lowest water level), the average width of vegetated area in the AA that separates adjoining uplands from open water within the AA is:"},null,null,null,{"$f":"IF((AllSat+AllSat>0),\"\", IF((OpenW=0),\"\", IF((SmallAA=1),\"\", MAX(F62:F66)/MAX(E62:E66))))","v":""},"Vwidth14","Wider vegetated zones within wetlands provide more nesting space and structure for songbirds and mammals. Avian species richness and abundance increase with riparian width (Keller et al.1993; Darveau et al.1995; Dickson et al.1995; Hodges and Krementz 1996). Wider riparian buffers in British Columbia supported a greater density of deciduous trees important to wildlife diversity (Shirley 2004). The diversity of microhabitats within bogs and fens generally increases with increasing area, and vertebrate richness consequently increases (Desrochers & van Duinen 2006). In calculations, is excluded automatically (cell goes blank) if wetland never has surface water during an average year or if wetland lacks open water or is <0.01 ha."]
[null,null,{"$f":"F!C85","v":"<1 m"},{"$f":"F!D85","v":0},0,{"$f":"D62*E62","v":0}]
[null,null,{"$f":"F!C86","v":"1 - 9 m"},{"$f":"F!D86","v":0},1,{"$f":"D63*E63","v":0}]
[null,null,{"$f":"F!C87","v":"10 - 29 m"},{"$f":"F!D87","v":0},3,{"$f":"D64*E64","v":0}]
[null,null,{"$f":"F!C88","v":"30 - 49 m"},{"$f":"F!D88","v":0},5,{"$f":"D65*E65","v":0}]
[null,null,{"$f":"F!C90","v":"> 100 m"},{"$f":"F!D90","v":0},6,{"$f":"D66*E66","v":0}]
[{"$f":"F!A95","v":"F18"},{"$f":"F!B95","v":"Interspersion of Robust Emergents & Open Water"},{"$f":"F!C95","v":"During most of the growing season, the spatial pattern of tall robust herbaceous vegetation (e.g., cattail, bulrush) that has surface water beneath it is mostly:"},null,null,null,{"$f":"IF((AllSat+AllSat>0),\"\",IF((NoPonded=1),\"\",IF((NoOpenPonded+NoOpenPonded1>0),\"\",IF((AllOpenPond=1),\"\", IF((SmallAA=1),\"\", MAX(F68:F70)/MAX(E68:E70))))))","v":0},"Interspers14","When water and vegetation (especially woody or other robust vegetation) are moderately interspersed, this provides more extensive feeding areas for many wetland-dependent songbirds and raptors. In calculations, is excluded automatically (cell goes blank) if wetland never has surface water during an average year, if no ponded water, if ponded water but no vegetation, if ponded but no open water, or if <0.01 ha."]
[null,null,{"$f":"F!C96","v":"Scattered in small clumps, islands, or patches throughout the surface water area."},{"$f":"F!D96","v":0},3,{"$f":"D68*E68","v":0}]
[null,null,{"$f":"F!C97","v":"Intermediate"},{"$f":"F!D97","v":0},2,{"$f":"D69*E69","v":0}]
[null,null,{"$f":"F!C98","v":"Clumped at one or a few sides of the surface water area, or mostly surrounds a central area of open water.  Or such vegetation is absent or covers <9 sq m and <1% of the AA."},{"$f":"F!D98","v":0},1,{"$f":"D70*E70","v":0}]
[{"$f":"F!A103","v":"F23"},{"$f":"F!B103","v":"Beaver Probability"},{"$f":"F!C103","v":"Use of the AA by beaver during the past 5 years is (select most applicable ONE):"},null,null,null,{"$f":"IF((AllSat+AllSat>0),\"\", MAX(F72:F75)/MAX(E72:E75))","v":0},"Beaver14a","Beaver impoundments, especially after they are abandoned and revert to early successional shrubs, are very species-rich compared with other land cover types (Grover & Baldassarre 1995, Aznar & Desrochers 2008). In calculations, is excluded automatically (cell goes blank) if wetland never has surface water during an average year."]
[null,null,{"$f":"F!C104","v":"evident from direct observation or presence of gnawed limbs, dams, tracks, dens, lodges, or extensive stands of water-killed trees (snags)."},{"$f":"F!D104","v":0},5,{"$f":"D72*E72","v":0}]
[null,null,{"$f":"F!C105","v":"likely based on known occurrence in the region and proximity to suitable habitat, which may include: (a) a persistent freshwater wetland, pond, or lake, or a perennial low or mid-gradient (<10%) channel, and (b) a corridor or multiple stands of hardwood trees and shrubs in vegetated areas near surface water."},{"$f":"F!D105","v":0},2,{"$f":"D73*E73","v":0}]
[null,null,{"$f":"F!C106","v":"unlikely because site characteristics above are deficient, and/or this is a settled area or other area where beaver are routinely removed.  But beaver occur in this part of the region (i.e., within 25 km)."},{"$f":"F!D106","v":0},1,{"$f":"D74*E74","v":0}]
[null,null,{"$f":"F!C107","v":"none.  Beaver are absent from this part of the region."},{"$f":"F!D107","v":0},0,{"$f":"D75*E75","v":0}]
[{"$f":"F!A134","v":"F30"},{"$f":"F!B134","v":"Total Woody Cover -% of the Vegetated AA"},{"$f":"F!C134","v":"Within the entire vegetated part of the AA, the percentage occupied by trees or shrubs taller than 1 m is:"},null,null,null,{"$f":"MAX(F77:F81)/MAX(E77:E81)","v":0},"WoodyPct14","Woody vegetation provides vertical structure that enables more individuals and species to inhabit a wetland.  It also provides shelter from weather and cover from predators."]
[null,null,{"$f":"F!C135","v":"<5% of the vegetated AA, or there is no woody vegetation in the AA.  SKIP to F38 (N Fixers)"},{"$f":"F!D135","v":0},0,{"$f":"D77*E77","v":0}]
[null,null,{"$f":"F!C136","v":"5-25%.  "},{"$f":"F!D136","v":0},1,0]
[null,null,{"$f":"F!C137","v":"25-50%"},{"$f":"F!D137","v":0},2,0]
[null,null,{"$f":"F!C138","v":"50-75%"},{"$f":"F!D138","v":0},2,0]
[null,null,{"$f":"F!C139","v":">75%"},{"$f":"F!D139","v":0},1,0]
[{"$f":"F!A140","v":"F31"},{"$f":"F!B140","v":"Interspersion of Herbaceous and Woody Cover"},{"$f":"F!C140","v":"The following best represents the distribution pattern of woody vegetation VS. unshaded herbaceous/ moss vegetation within the AA:"},null,null,null,{"$f":"MAX(F83:F86)/MAX(E83:E86)","v":0},"HerbWoodMix14","Interspersion of woody cover with food-rich openings of herbaceous vegetation provides greater feeding opportunities for many songbirds and mammals, and is a natural phenomenon caused by windthrow and other factors in forested wetlands. Excessive gap frequencies and areas (i.e., forest fragmentation) and lack of corridors that connect forested wetlands with upland forests can be detrimental to some species if the remaining forested patches are very small."]
[null,null,{"$f":"F!C141","v":"(a) Woody cover and herbaceous/ moss cover EACH comprise 30-70% of the vegetated part of the AA, AND (b) There are many patches of woody vegetation scattered widely within herbaceous/ moss vegetation, or many patches of herbaceous vegetation scattered widely within woody vegetation."},{"$f":"F!D141","v":0},3,{"$f":"D83*E83","v":0}]
[null,null,{"$f":"F!C142","v":"(a) Woody cover and herbaceous/ moss EACH comprise 30-70% of the vegetated AA, AND (b) There are few patches (\"islands\") of woody vegetation scattered widely within herbaceous vegetation, or few patches of herbaceous/ moss vegetation (\"gaps\") scattered widely within woody vegetation."},{"$f":"F!D142","v":0},2,{"$f":"D84*E84","v":0}]
[null,null,{"$f":"F!C143","v":"(a) Woody cover OR herbaceous/ moss comprise >70% of the vegetated AA, AND (b) There are several patches of the other scattered within it. "},{"$f":"F!D143","v":0},1,{"$f":"D85*E85","v":0}]
[null,null,{"$f":"F!C144","v":"(a) Woody cover OR herbaceous/ moss comprise >70% of the vegetated AA, AND (b) The other is absent or is mostly in a single area or distinct zone with almost no intermixing of woody and unshaded herbaceous/ moss vegetation."},{"$f":"F!D144","v":0},0,{"$f":"D86*E86","v":0}]
[{"$f":"F!A145","v":"F32"},{"$f":"F!B145","v":"Tall Woody Canopy- % of the Vegetated AA"},{"$f":"F!C145","v":"Within the vegetated part of the AA, just the woody plants taller than 3 m occupy:"},null,null,null,{"$f":"IF((NoWoodyVeg=1),\"\", MAX(F88:F92)/MAX(E88:E92))","v":0},"TreePct14","Trees support a wider diversity of songbirds, raptors, and mammals than does herbaceous vegetation, partly because they provide more vertical structure and produce downed wood and snags that have other habitat benefits. Trees help shelter the water in wetlands from high winds, facilitating the aerial foraging activities of birds and bats (Whitaker et al. 2000).  However, a mix of tree and shrub cover usually promotes greater habitat structure and songbird diversity overall. In calculations, is excluded automatically (cell goes blank) if woody vegetation is <5% of the vegetated part of the AA."]
[null,null,{"$f":"F!C146","v":"<1% of the vegetated AA, or the AA lacks trees.  Enter \"1\" and SKIP to F35 (Exposed Shrub)."},{"$f":"F!D146","v":0},0,{"$f":"D88*E88","v":0}]
[null,null,{"$f":"F!C147","v":"1-25% of the vegetated AA"},{"$f":"F!D147","v":0},1,{"$f":"D89*E89","v":0}]
[null,null,{"$f":"F!C148","v":"25-50% of the vegetated AA"},{"$f":"F!D148","v":0},2,{"$f":"D90*E90","v":0}]
[null,null,{"$f":"F!C149","v":"50-95% of the vegetated AA"},{"$f":"F!D149","v":0},3,{"$f":"D91*E91","v":0}]
[null,null,{"$f":"F!C150","v":">95% of the vegetated part of the AA"},{"$f":"F!D150","v":0},2,{"$f":"D92*E92","v":0}]
[{"$f":"F!A151","v":"F33"},{"$f":"F!B151","v":"Woody Diameter Classes"},{"$f":"F!C151","v":"Mark all the classes of woody plants within the AA, but only IF they comprise more than 5% of the woody canopy within the AA.  Do not count trees that adjoin but are not within the AA."},null,null,null,{"$f":"IF((NoWoodyVeg=1),\"\",IF((NoTrees=1),\"\",((SUM(D94:D101)/8+ MAX(F94:F101)/MAX(E94:E101))/2)))","v":0},"TreeTypes14","Tree cavities needed by many nesting songbirds and mammals are found mostly in dead standing trees (snags) and larger-diameter trees, which are more likely to have bole entries, conks, abundant mistletoe, and dead tops (Bakker & Hastings 2002.) Larger-diameter stands also tend to be older and provide more structure useful to a variety of songbirds and mammals. Tall snags are especially useful to raptors as hunting perches. A mixture of tree species, especially mixtures that include aspen, is necessary to sustain populations of most boreal woodpecker species [Drever & Martin 2010]. Deer need a diversity of forest types and ages (both clear-cut and old growth) near each other within their home ranges. In calculations, is excluded automatically (cell goes blank) if trees occupy <5% of the vegetated part of the AA.  Otherwise, score is based on the number of categories and a weighted average that favors larger deciduous trees.\n"]
[null,null,{"$f":"F!C152","v":"coniferous, 1-9 cm diameter and >1 m tall"},{"$f":"F!D152","v":0},1,{"$f":"D94*E94","v":0}]
[null,null,{"$f":"F!C153","v":"broad-leaved deciduous 1-9 cm diameter and >1 m tall"},{"$f":"F!D153","v":0},3,0]
[null,null,{"$f":"F!C154","v":"coniferous, 10-19 cm diameter"},{"$f":"F!D154","v":0},2,0]
[null,null,{"$f":"F!C155","v":"broad-leaved deciduous 10-19 cm diameter"},{"$f":"F!D155","v":0},4,0]
[null,null,{"$f":"F!C156","v":"coniferous, 20-40 cm diameter"},{"$f":"F!D156","v":0},3,0]
[null,null,{"$f":"F!C157","v":"broad-leaved deciduous 20-40 cm diameter"},{"$f":"F!D157","v":0},6,0]
[null,null,{"$f":"F!C158","v":"coniferous, >40 cm diameter"},{"$f":"F!D158","v":0},5,0]
[null,null,{"$f":"F!C159","v":"broad-leaved deciduous >40 cm diameter"},{"$f":"F!D159","v":0},8,0]
[{"$f":"F!A160","v":"F34"},{"$f":"F!B160","v":"Downed Wood"},{"$f":"F!C160","v":"The number of downed wood pieces longer than 2 m and with diameter >10 cm, and not persistently submerged, is:"},null,null,null,{"$f":"IF((NoWoodyVeg=1),\"\", IF((NoTrees=1),\"\", MAX(F103:F104)))","v":0},"WoodDown14","Downed wood provides cover for many small mammals. Downed wood is often the result of natural windthrow, which also creates small patches of semi-open canopy within blocks of forest and in so doing can support a larger number of wildlife species, despite the temporary loss of nest trees (Zmihorski 2010).  In calculations, is excluded automatically (cell goes blank) if woody vegetation is <5% of the vegetated part of the AA."]
[null,null,{"$f":"F!C161","v":"Several ( >5 if AA is >5 hectares, less for smaller AAs)"},{"$f":"F!D161","v":0},1,{"$f":"D103*E103","v":0}]
[null,null,{"$f":"F!C162","v":"Few or none "},{"$f":"F!D162","v":0},0,{"$f":"D104*E104","v":0}]
[{"$f":"F!A163","v":"F35"},{"$f":"F!B163","v":"Exposed Shrub Canopy"},{"$f":"F!C163","v":"Woody vegetation 1 to 3 m tall that is not under the drip line of taller woody vegetation comprises:"},null,null,null,{"$f":"IF((NoWoodyVeg=1),\"\", MAX(F106:F110)/MAX(E106:E110))","v":0},"ShrubCanop14","Shrubs that are not under a tree canopy are preferred by many nesting songbirds, such as song sparrow, Lincoln's sparrow, and orange-crowned warbler. In calculations, is excluded automatically (cell goes blank) if woody vegetation is <5% of the vegetated part of the AA."]
[null,null,{"$f":"F!C164","v":"<5% of the vegetated AA and (if a fringe wetland) <5% of its water edge.  Or <0.01 hectare.  SKIP to F38 (N Fixers)."},{"$f":"F!D164","v":0},0,{"$f":"D106*E106","v":0}]
[null,null,{"$f":"F!C165","v":"5-25% of the vegetated AA or (if a fringe wetland) 5-25% of the water edge  -- whichever is greater."},{"$f":"F!D165","v":0},2,{"$f":"D107*E107","v":0}]
[null,null,{"$f":"F!C166","v":"25-50% of the vegetated AA or the water edge, whichever is greater. "},{"$f":"F!D166","v":0},3,{"$f":"D108*E108","v":0}]
[null,null,{"$f":"F!C167","v":"50-95% of the vegetated AA or the water edge, whichever is greater."},{"$f":"F!D167","v":0},3,{"$f":"D109*E109","v":0}]
[null,null,{"$f":"F!C168","v":">95% of the vegetated part of the AA or the water edge, whichever is greater."},{"$f":"F!D168","v":0},2,{"$f":"D110*E110","v":0}]
[{"$f":"F!A169","v":"F36"},{"$f":"F!B169","v":"Dominance of Most Abundant Shrub Species "},{"$f":"F!C169","v":"Determine which two native shrub species (1 to 3 m tall) comprise the greatest portion of the native shrub cover.  Then choose one of the following:"},null,null,null,{"$f":"IF((NoWoodyVeg=1),\"\",IF((NoShrub=1),\"\", MAX(F112:F113)/MAX(E112:E113)))","v":0},"ShrubDiv14","Lack of one dominant shrub species suggests higher shrub richness, which has the potential to provide more food sources to more species throughout a season. In calculations, is excluded automatically (cell goes blank) if exposed shrub cover is <5% of the vegetated part of the AA."]
[null,null,{"$f":"F!C170","v":"those species together comprise > 50% of the areal cover of native shrub species."},{"$f":"F!D170","v":0},1,{"$f":"D112*E112","v":0}]
[null,null,{"$f":"F!C171","v":"those species together do not comprise > 50% of the areal cover of native shrub species."},{"$f":"F!D171","v":0},2,{"$f":"D113*E113","v":0}]
[{"$f":"F!A172","v":"F37"},{"$f":"F!B172","v":"Broad-leaved Deciduous Trees and Shrubs"},{"$f":"F!C172","v":"The percentage of the AA's tree or shrub cover that is broad-leaved deciduous and is taller than 1 meter is:"},null,null,null,{"$f":"IF((NoWoodyVeg=1),\"\",MAX(F115:F119)/MAX(E115:E119))","v":0},"Hardwd14","At least in regions dominated by conifers, deciduous shrub cover is known to increase local bird richness and probably abundance (Willson & Comet 1996a,b).  In calculations, is excluded automatically (cell goes blank) if woody vegetation is <5% of the vegetated part of the AA."]
[null,null,{"$f":"F!C173","v":"<1%, or largest patch occupies less than 0.01 hectare"},{"$f":"F!D173","v":0},0,{"$f":"D115*E115","v":0}]
[null,null,{"$f":"F!C174","v":"1-25% of the tree or shrub cover (whichever has more)"},{"$f":"F!D174","v":0},1,{"$f":"D116*E116","v":0}]
[null,null,{"$f":"F!C175","v":"25-50% of the tree or shrub cover (whichever has more)"},{"$f":"F!D175","v":0},2,{"$f":"D117*E117","v":0}]
[null,null,{"$f":"F!C176","v":"50-75% of the tree or shrub cover (whichever has more)"},{"$f":"F!D176","v":0},3,{"$f":"D118*E118","v":0}]
[null,null,{"$f":"F!C177","v":">75% of the tree or shrub cover (whichever has more)"},{"$f":"F!D177","v":0},4,{"$f":"D119*E119","v":0}]
[{"$f":"F!A184","v":"F39"},{"$f":"F!B184","v":"Snags"},{"$f":"F!C184","v":"The number of large snags (diameter >20 cm) in the AA plus the upland area within 10 m of the wetland edge is:"},null,null,null,{"$f":"IF((NoWoodyVeg=1),\"\", IF((NoTrees=1),\"\", MAX(F121:F123)/MAX(E121:E123)))","v":0},"SnagD14","Tree cavities are needed by many nesting songbirds and mammals, and by roosting bats. Tall snags are especially useful to raptors as hunting perches."]
[null,null,{"$f":"F!C185","v":"Several ( >2/hectare) and a pond, lake, or slow-flowing water wider than 10 m is within 1 km."},{"$f":"F!D185","v":0},2,{"$f":"D121*E121","v":0}]
[null,null,{"$f":"F!C186","v":"Several ( >2/hectare) but above not true."},{"$f":"F!D186","v":0},1,{"$f":"D122*E122","v":0}]
[null,null,{"$f":"F!C187","v":"Few or none "},{"$f":"F!D187","v":0},0,{"$f":"D123*E123","v":0}]
[{"$f":"F!A204","v":"F43"},{"$f":"F!B204","v":"Upland Inclusions"},{"$f":"F!C204","v":"Within the AA, inclusions of upland that individually are >100 sq.m. are:"},null,null,null,{"$f":"IF((D125=1),\"\", MAX(F125:F127)/MAX(E125:E127))","v":0},"Inclus14","Wetlands with upland inclusions allow animals to move more conveniently between uplands and wetlands, using resources in each."]
[null,null,{"$f":"F!C205","v":"Few or none"},{"$f":"F!D205","v":0},0,{"$f":"D125*E125","v":0}]
[null,null,{"$f":"F!C206","v":"Intermediate (1 - 10% of vegetated part of the AA)."},{"$f":"F!D206","v":0},1,{"$f":"D126*E126","v":0}]
[null,null,{"$f":"F!C207","v":"Many (e.g., wetland-upland \"mosaic\", >10% of the vegetated AA)."},{"$f":"F!D207","v":0},2,{"$f":"D127*E127","v":0}]
[{"$f":"F!A224","v":"F47"},{"$f":"F!B224","v":"Forb Cover"},{"$f":"F!C224","v":"The areal cover of forbs reaches an annual maximum of:"},null,null,null,{"$f":"IF((NoHerbCov=1),\"\", MAX(F129:F133)/MAX(E129:E133))","v":0},"ForbCov14","Forbs are an important component of the foods that a wide variety of songbirds and mammals require. In calculations, is excluded automatically (cell goes blank) if herbaceous cover is <5% of the vegetated cover."]
[null,null,{"$f":"F!C225","v":"<5% of the herbaceous & moss cover"},{"$f":"F!D225","v":0},0,{"$f":"D129*E129","v":0}]
[null,null,{"$f":"F!C226","v":"5-25% of the herbaceous & moss cover"},{"$f":"F!D226","v":0},2,{"$f":"D130*E130","v":0}]
[null,null,{"$f":"F!C227","v":"25-50% of the herbaceous & moss cover"},{"$f":"F!D227","v":0},3,{"$f":"D131*E131","v":0}]
[null,null,{"$f":"F!C228","v":"50-95% of the herbaceous & moss cover"},{"$f":"F!D228","v":0},2,{"$f":"D132*E132","v":0}]
[null,null,{"$f":"F!C229","v":">95% of the herbaceous & moss cover. SKIP to F50 (Invasive Plant Cover)."},{"$f":"F!D229","v":0},1,{"$f":"D133*E133","v":0}]
[{"$f":"F!A230","v":"F48"},{"$f":"F!B230","v":"Sedge Cover"},{"$f":"F!C230","v":"Sedges (Carex spp.) and/or cottongrass (Eriophorum spp.) occupy:"},null,null,null,{"$f":"IF((NoHerbCov=1),\"\", MAX(F135:F138)/MAX(E135:E138))","v":0},"Sedge14"," Sedges are favored as forage by many wetland mammals. In calculations, is excluded automatically (cell goes blank) if herbaceous cover is <5% of the vegetated cover."]
[null,null,{"$f":"F!C231","v":"<5% of the herbaceous cover, or <0.01 hectare"},{"$f":"F!D231","v":0},0,{"$f":"D135*E135","v":0}]
[null,null,{"$f":"F!C232","v":"5-50% of the herbaceous cover"},{"$f":"F!D232","v":0},3,0]
[null,null,{"$f":"F!C233","v":"50-95% of the herbaceous cover"},{"$f":"F!D233","v":0},2,0]
[null,null,{"$f":"F!C234","v":">95% of the herbaceous cover"},{"$f":"F!D234","v":0},1,0]
[{"$f":"F!A235","v":"F49"},{"$f":"F!B235","v":"Dominance of Most Abundant Herbaceous Species "},{"$f":"F!C235","v":"Determine which two native herbaceous (forb and graminoid) species comprise the greatest portion of the herbaceous cover that is unshaded by a woody canopy.  Then choose one of the following:"},null,null,null,{"$f":"IF((D141=1),1,\"\")","v":""},"HerbDom14","Multiple herb species, none strongly dominant, provide a wider range of foods throughout the growing season for wetland songbirds and mammals. Included in calculations only if herbaceous cover is >5% of vegetated cover and second choice is answered positively."]
[null,null,{"$f":"F!C236","v":"those species together comprise > 50% of the areal cover of native herbaceous plants at any time during the year."},{"$f":"F!D236","v":0}]
[null,null,{"$f":"F!C237","v":"those species together do not comprise > 50% of the areal cover of native herbaceous plants at any time during the year."},{"$f":"F!D237","v":0}]
[{"$f":"F!A249","v":"F52"},{"$f":"F!B249","v":"Natural Cover in Buffer"},{"$f":"F!C249","v":"Along the wetland-upland edge and extending 30 m upslope, the percentage of the upland that contains natural (not necessarily native -- see column E) land cover taller than 10 cm is:"},null,null,null,{"$f":"MAX(F143:F147)/MAX(E143:E147)","v":0},"CUbuffNatPct14","Upland cover with perennial vegetation is very important to many songbirds and mammals that occur in wetlands or along a wetland's upland edge. Some landbirds in Southeast Alaska may need buffers of over 1000 ft. (Kissling & Garton 2008). Wetlands that contain or are close to natural land cover, and not separated from that by roads that interfere with movements across the landscape, are more likely to support forest-dwelling species. The probability that a forest-dwelling bird will fly in the open between two patches of forest decreases rapidly as the distance separating those patches increases (Desrochers & Hannon 1997, St. Clair et al. 1998). Forest bird species usually prefer to detour under forest cover even if the forested route is longer, but if the detour is too long, they will prefer a shortcut across openland. However, when possible most forest bird species avoid venturing farther than about 100 ft from a forest edge (St. Clair et al. 1998)."]
[null,null,{"$f":"F!C250","v":"<5% "},{"$f":"F!D250","v":0},0,{"$f":"D143*E143","v":0}]
[null,null,{"$f":"F!C251","v":"5 to 30%"},{"$f":"F!D251","v":0},1,{"$f":"D144*E144","v":0}]
[null,null,{"$f":"F!C252","v":"30 to 60%"},{"$f":"F!D252","v":0},2,{"$f":"D145*E145","v":0}]
[null,null,{"$f":"F!C253","v":"60 to 90%"},{"$f":"F!D253","v":0},4,{"$f":"D146*E146","v":0}]
[null,null,{"$f":"F!C254","v":">90%.  SKIP to F54 (Cliffs)."},{"$f":"F!D254","v":0},5,{"$f":"D147*E147","v":0}]
[{"$f":"F!A255","v":"F53"},{"$f":"F!B255","v":"Type of Cover in Buffer"},{"$f":"F!C255","v":"Within 30 m upslope of the wetland-upland edge closest to the AA, the upland land cover that is NOT unmanaged vegetation or water is mostly (mark ONE):"},null,null,null,{"$f":"IF((BuffAllNat=1),\"\", MAX(F149:F150)/MAX(E149:E150))","v":0},"CUtypeLU14","Small mammals moving between wetlands are less likely to have their movements disrupted by lands with residual cover than in lands with impervious surface. In calculations, is excluded automatically (cell goes blank) if natural cover in the buffer (see above) is >90%."]
[null,null,{"$f":"F!C256","v":"impervious surface, e.g., paved road, parking lot, building, exposed rock."},{"$f":"F!D256","v":0},0,{"$f":"D149*E149","v":0}]
[null,null,{"$f":"F!C257","v":"bare or nearly bare pervious surface or managed vegetation, e.g., lawn, annual crops, mostly-unvegetated clearcut, landslide, unpaved road, dike."},{"$f":"F!D257","v":0},1,{"$f":"D150*E150","v":0}]
[{"$f":"F!A258","v":"F54"},{"$f":"F!B258","v":"Cliffs, Steep Banks, or Salt Lick "},{"$f":"F!C258","v":"In the AA or within 100 m, there is a known salt lick, or elevated terrestrial features such as cliffs, talus slopes, stream banks, or excavated pits (but not riprap) that extend at least 2 m nearly vertically, are unvegetated, and potentially contain crevices or other substrate suitable for nesting or den areas.  Enter 1 (yes) or 0 (no)."},{"$f":"F!D258","v":0},1,{"$f":"D151*E151","v":0},{"$f":"IF((D151=0),\"\",1)","v":""},"Cliffs14","Some of these features are important to bank-living beavers, swallows, and swifts."]
[{"$f":"F!A280","v":"F59"},{"$f":"F!B280","v":"Unvisited Core Area "},{"$f":"F!C280","v":"The percentage of the AA almost never visited by humans during an average growing season probably comprises: [Note: Do not include visitors on trails outside of the AA unless more than half the wetland is visible from the trails and they are within 30 m of the wetland edge.  In that case, imagine the percentage of the AA that would be covered by the trail if it were placed within the AA.]"},null,null,null,{"$f":"MAX(F153:F158)/MAX(E153:E158)","v":0},"Core14a","Human presence can attract crows and ravens, which prey on nests. Dogs and house cats which prey on wetland songbirds and mammals also tend to be more prevalent in areas frequently visited by humans."]
[null,null,{"$f":"F!C281","v":"<5% and no inhabited building is within 100 m of the AA"},{"$f":"F!D281","v":0},1,{"$f":"D153*E153","v":0}]
[null,null,{"$f":"F!C282","v":"<5% and inhabited building is within 100 m of the AA"},{"$f":"F!D282","v":0},0,0]
[null,null,{"$f":"F!C283","v":"5-50% and no inhabited building is within 100 m of the AA"},{"$f":"F!D283","v":0},3,0]
[null,null,{"$f":"F!C284","v":"5-50% and inhabited building is within 100 m of the AA"},{"$f":"F!D284","v":0},2,0]
[null,null,{"$f":"F!C285","v":"50-95%"},{"$f":"F!D285","v":0},4,0]
[null,null,{"$f":"F!C286","v":">95% of the AA"},{"$f":"F!D286","v":0},5,0]
[{"$f":"F!A287","v":"F60"},{"$f":"F!B287","v":"Frequently Visited Area"},{"$f":"F!C287","v":"The percentage of the AA visited by humans almost daily for several weeks during an average growing season probably comprises: [Note: Do not include visitors on trails outside of the AA unless more than half the wetland is visible from the trails and they are within 30 m of the wetland edge.   In that case, imagine the percentage of the AA that would be covered by the trail if it were placed within the AA.]"},null,null,null,{"$f":"MAX(F160:F163)/MAX(E160:E163)","v":0},"Core14b","See above."]
[null,null,{"$f":"F!C288","v":"<5%.  If F59 was answered \">95%\", SKIP to F63 (Consumptive Uses)."},{"$f":"F!D288","v":0},3,{"$f":"D160*E160","v":0}]
[null,null,{"$f":"F!C289","v":"5-50%"},{"$f":"F!D289","v":0},2,{"$f":"D161*E161","v":0}]
[null,null,{"$f":"F!C290","v":"50-95%"},{"$f":"F!D290","v":0},1,{"$f":"D162*E162","v":0}]
[null,null,{"$f":"F!C291","v":">95% of the AA"},{"$f":"F!D291","v":0},0,{"$f":"D163*E163","v":0}]
[{"$f":"F!A293","v":"F62"},{"$f":"F!B293","v":"BMP - Wildlife Protection"},{"$f":"F!C293","v":"Fences, observation blinds, platforms, paved trails, exclusion periods, and/or well-enforced prohibitions on motorized boats, off-leash pets, and off road vehicles appear to effectively exclude or divert visitors and their pets from the AA at critical times in order to minimize disturbance of wildlife (except during hunting seasons).  Enter \"1\" if true. "},{"$f":"F!D293","v":0},null,null,{"$f":"IF((D158+D160>1),\"\",D164)","v":0},"BMP_14","Human presence can attract crows and ravens, which prey on nests. In calculations, is excluded automatically (cell goes blank) if last choice in F59 was chosen AND first choice in F60 was chosen."]
[{"$f":"F!A328","v":"F69"},{"$f":"F!B328","v":"Plants or Animals of Conservation Concern"},{"$f":"F!C328","v":"If required, survey the AA for plant or animal species believed to be of conservation concern in Alberta (see list on Form F in Appendix A of Manual).  Do so at appropriate times of the year, especially if the data review conducted during the office phase of this assessment indicated their past presence in the general vicinity.  If you do detect these species or have reliable knowledge of their recent (within ~5 years) occurrence within the AA, indicate that below.  "},null,null,null,null,null,"Because of their relative rarity, these songbird, raptor, and mammal species contribute more to regional biodiversity than ones with broader habitat tolerances."]
[null,null,{"$f":"F!C333","v":"One or more of the rare songbird or mammal species was detected within the AA."},{"$f":"F!D333","v":0},null,null,{"$f":"IF((D166=1),1,\"\")","v":""},"RareSBM"]
[]
[null,null,"Habitat Structure [HabStrucS]"]
[null,"Wetlands <10 hectares:","[ AVERAGE(WetVegArea, Vwidth14, ClassRichIn14) + AVERAGE(WetPerim2Area, Inclus14) + AVERAGE(WatProb, SatPct14, PondedOWpct14) + AVERAGE(WoodyPct14, TreePct14, ShrubCanop14, ShrubDiv14, HerbDom14, TreeTypes14, SnagD14, WoodDown14, Cliffs14) + AVERAGE(Interspers14, WoodPatt14)] / 5",null,null,null,{"$f":"IF((GT10HA=1),G170, IFERROR((AVERAGE(WetVegArea, Vwidth14, ClassRichIn14) + AVERAGE(WetPerim2Area, Inclus14) + AVERAGE(WatProb, SatPct14, PondedOWpct14) + AVERAGE(WoodyPct14, TreePct14, ShrubCanop14, ShrubDiv14, HerbDom14, TreeTypes14, SnagD14, WoodDown14, Cliffs14) + AVERAGE(Interspers14, WoodPatt14)) /5,\"\"))","v":0.05}]
[null,"Wetlands >10 hectares:","Substituted ClassRichIn, 1-OWpct, WetWooded, MixWaterVeg, MixHerbWood",null,null,null,{"$f":"IFERROR((AVERAGE(WetVegArea, Vwidth14, ClassRichIn) + AVERAGE(WetPerim2Area, Inclus14) + AVERAGE(1-WatProb, SatPct14,1- OWpct) + AVERAGE(WetWooded, ShrubCanop14, ShrubDiv14, HerbDom14, TreeTypes14, SnagD14, WoodDown14, Cliffs14) + AVERAGE(MixWaterVeg, MixHerbWood)) /5,\"\")","v":""}]
[]
[null,null,"Habitat Productivity [CfixS]"]
[null,"Wetlands <10 hectares:","[ MAX(RaptorNest, BioDivZone, Spring) + AVERAGE(GrowDD, RipFloodpl, Wettype14, Hardwd14, Sedge14, ForbCov14, Beaver14a)] /2",null,null,null,{"$f":"IF((GT10HA=1),G174, IFERROR((MAX(RaptorNest, BioDivZone, Spring) + AVERAGE(GrowDD, RipFloodpl, Wettype14, Hardwd14, Sedge14, ForbCov14,  Beaver14a)) /2,\"\"))","v":0}]
[null,"Wetlands >10 hectares:","Substituted FenMarshSwamp",null,null,null,{"$f":"IFERROR((MAX(RaptorNest, BioDivZone, Spring) + AVERAGE(GrowDD, RipFloodpl, FenMarshSwamp, Hardwd14, Sedge14, ForbCov14,  Beaver14)) /2,\"\")","v":0}]
[]
[null,null,"Offsite Habitat Influence [LscapeS]"]
[null,null,"AVERAGE(PerimNatCov, NatCov1k, ClassRich1k, WetDens1k, VegCon1k, CUbuffNatPct14)",null,null,null,{"$f":"IFERROR(AVERAGE(PerimNatCov, NatCov1k, ClassRich1k, WetDens1k, VegCon1k, CUbuffNatPct14),\"\")","v":0}]
[]
[null,null,"Stressors (Lack of)  [StressS]"]
[null,null,"AVERAGE(1-WQrisk, Dist2DevCrop, 1-WindWin, 1-RdDens1k, DistRd, DistPop, Core14a, Core14b, BMP_14)",null,null,null,{"$f":"IFERROR(AVERAGE(1-WQrisk, Dist2DevCrop, 1-WindWin, 1-RdDens1k, Dist2Road, DistPop, Core14a, Core14b, BMP_14),\"\")","v":0.5}]
[]
[null,null,"ABWRET-A FUNCTION MODEL"]
[null,null,"Songbird, Raptor, and Mammal Habitat"]
[null,null,"IF((RareSBM=1),10, ELSE: 10*AVERAGE(UniqClass, HabStrucS, CfixS,  LscapeS, StressS))",null,null,null,{"$f":"IF((RareSBM=1),10, 10*AVERAGE(UniqClass,HabStrucS1a, CfixS1a, LscapeS1a, StressS1a))","v":1.375}]
[null,null,null,null,null,null,null,null,"Literature Cited"]
[null,null,"ABWRET-E model:",null,null,null,null,null,"Andren, H. 1994. Effects of habitat fragmentation on birds and mammals in landscapes with different proportions of suitable habitat – a review. Oikos 71:355-366."]
[null,1,"Calculate these averages:",null,null,null,null,null,"Awade, M. and J. P. Metzger. 2008. Using gap-crossing capacity to evaluate functional connectivity of two Atlantic rainforest birds and their response to fragmentation. Austral Ecology 33:863 - 871."]
[null,"a","AVERAGE(WetVegArea,ClassRichIn) ",{"$f":"IFERROR(AVERAGE(WetVegArea,ClassRichIn),\"\")","v":""},null,null,null,null,"Aznar, J. C. and A. Desrochers. 2008. Building for the future: Abandoned beaver ponds promote bird diversity. Ecoscience 15:250-257."]
[null,"b","AVERAGE(MixHerbWood, MixWaterVeg, MarshFenSwamp, 1-OWpct)",{"$f":"IFERROR(AVERAGE(MixHerbWood, MixWaterVeg, MarshFenSwamp,1- OWpct),\"\")","v":1},null,null,null,null,"Bakker, V. J. and D. H. Van Vuren. 2004. Gap‐crossing decisions by the red squirrel, a forest‐dependent small mammal. Conservation Biology 18:689-697."]
[null,"c","AVERAGE (ClassRich1k, WetDens1k)",{"$f":"IFERROR(AVERAGE(ClassRich1k, WetDens1k),\"\")","v":""},null,null,null,null,"Barber, J. R., K. R. Crooks, and K. M. Fristrup. 2010. The costs of chronic noise exposure for terrestrial organisms. Trends in Ecology & Evolution 25:180-189."]
[null,"d","AVERAGE(BiodivZone, RaptorNest, RipFloodpl)",{"$f":"IFERROR(AVERAGE(BioDivZone, RaptorNest, RipFloodpl),\"\")","v":""},null,null,null,null,"Belisle, M. and A. Desrochers. 2002. Gap-crossing decisions by forest birds: an empirical basis for parameterizing spatially-explicit, individual-based models. Landscape Ecology 17:219-231."]
[null,"e","AVERAGE (1-WindWin, Dist2DevCrop, NatCov1k, VegConn1k, DistRd, 1-RdDens1k) ",{"$f":"IFERROR(AVERAGE(1-WindWin, Dist2DevCrop, NatCov1k, VegCon1k, Dist2Road, 1-RdDens1k),\"\")","v":1},null,null,null,null,"Benitez-Lopez, A., R. Alkemade, and P. A. Verweij. 2010. The impacts of roads and other infrastructure on mammal and bird populations: A meta-analysis. Biological Conservation 143:1307-1316."]
[null,2,"10*AVERAGE(UniqClass, a, b, c, d, e)",{"$f":"10*AVERAGE(UniqClass, D188:D192)","v":10},null,null,null,null,"Bosschieter, L. and P. W. Goedhart. 2005. Gap crossing decisions by reed warblers (Acrocephalus scirpaceus) in agricultural landscapes. Landscape Ecology 20:455–468."]
[null,null,null,null,null,null,null,null,"Calmé, S. and A. Desrochers. 2000. Biogeographic aspects of the distribution of bird species breeding in Québec’s peatlands. Journal of Biogeography 27: 725–732."]
[null,null,"ABWRET-E with substitutions:",null,null,null,null,null,"Chace, J. F. and J. J. Walsh. 2006. Urban effects on native avifauna: a review. Landscape and Urban Planning 74:46-69."]
[null,1,"Calculate these averages:",null,null,null,null,null,"Clevenger, A. P., B. Chruszczc, and K. E. Gunson. 2003. Spatial patterns and factors influencing small vertebrate fauna road-kill aggregations. Biological Conservation 109:15-26."]
[null,"a","AVERAGE(WetVegArea,ClassRichIn) ",{"$f":"IFERROR(AVERAGE(WetVegArea,ClassRichIn),\"\")","v":""},null,null,null,null,"Creegan, H. P. and P. E. Osborne. 2005. Gap-crossing decisions of woodland songbirds in Scotland: an experimental approach. Journal of Applied Ecology 42:678-687."]
[null,"b","AVERAGE(WoodPatt14, Interspers14, MarshFenSwamp, PondedOWpct14)",{"$f":"IFERROR(IF((AllSat+AllSat>0),\"\",IF((SmallAA=1),\"\", AVERAGE(WoodPatt14, Interspers14, MarshFenSwamp,PondedOWpct14))),\"\")","v":0},null,null,null,null,"Darveau, M., P. Beauchesne, L. Belanger, J. Huot, and P. Larue. 1995. Riparian forest strips as habitat for breeding birds in boreal forest. The Journal of Wildlife Management:67-78."]
[null,"c","AVERAGE (ClassRich1km, WetDens1k)",{"$f":"IFERROR(AVERAGE(ClassRich1k, WetDens1k),\"\")","v":""},null,null,null,null,"De Santo, T. L. and M. F. Willson. 2001. Predator abundance and predation of artificial nests in natural and anthropogenic coniferous forest edges in southeast Alaska. Journal of Field Ornithology 72:136-149."]
[null,"d","AVERAGE(BiodivZone, RaptorNest, RipFloodpl)",{"$f":"IFERROR(AVERAGE(BioDivZone, RaptorNest, RipFloodpl),\"\")","v":""},null,null,null,null,"Desrochers, A. and S. J. Hannon. 1997. Gap crossing decisions by forest songbirds during the post-fledging period. Conservation Biology 11:1204-1210."]
[null,"e","AVERAGE (1-WindWint, DistDevCrop, NatCov1k, VegConn1k, DistRd, RdDens1k) ",{"$f":"IFERROR(AVERAGE(1-WindWin, Dist2DevCrop, NatCov1k, VegCon1k, Dist2Road, 1-RdDens1k),\"\")","v":1},null,null,null,null,"Desrochers, A. and G.-J. van Duinen. 2006. Peatland fauna. Pages 67-100 in R. K. Wieder and D. H. Vitt, editors. Boreal Peatland Ecosystems, Ecological Studies, Volume 188. Springer, Berlin Heidelberg, GE."]
[null,2,"10*AVERAGE(UniqClass, a, b, c, d, e)",{"$f":"10*AVERAGE(UniqClass, D197:D201)","v":5},null,null,null,null,"Dickson, J. G., J. H. Williamson, R. N. Conner, and B. Ortega. 1995. Streamside zones and breeding birds in east Texas. Wildlife Society Bulletin 23:750-755."]
[null,null,null,null,null,null,null,null,"Donnelly, R. and J. M. Marzluff. 2004. Importance of reserve size and landscape context to urban bird conservation. Conservation Biology 18:733-745."]
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[null,null,null,null,null,null,null,null,"Trevino, H. S., A. M. Skibiel, T. J. Karels, and F. S. Dobson. 2007. Threats to avifauna on oceanic islands. Conservation Biology 21:125–132."]
[null,null,null,null,null,null,null,null,"Trombulak, S. C. and C. A. Frissell. 2000. Review of ecological effects of roads on terrestrial and aquatic communities. Conservation Biology 14:18-30."]
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[null,null,null,null,null,null,null,null,"Whitaker, D. M., A. L. Carroll, and W. A. Montevecchi. 2000. Elevated numbers of flying insects and insectivorous birds in riparian buffer strips. Canadian Journal of Zoology 78:740-747."]
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["Native Plant & Pollinator Habitat",null,"The capacity to support or contribute to a diversity of native, hydrophytic, vascular plant species, communities, and/or functional groups.  As well, the capacity to support pollinating insects, such as bees, wasps, flies, butterflies, moths, and beetles.","PH"]
["#","Function Indicators from Estimator","Scoring Notes",null,null,null,"Normalised Score","Indicator Abbreviation or Formula","Rationale"]
[{"$f":"OF!A6","v":"OF5"},{"$f":"OF!C6","v":"Wetland Class Richness Within 1km"}," ",null,null,null,{"$f":"IF((ClassRich1k=\"\"),\"\",ClassRich1k)","v":""},"ClassRich1k","Because each wetland class has a distinct flora, a greater variety of wetland classes implies greater plant diversity and more diverse sources of pollen for pollinators."]
[{"$f":"OF!A7","v":"OF6"},{"$f":"OF!C7","v":"Wetland Class Richness Within Wetland"}," ",null,null,null,{"$f":"IF((ClassRichIn=\"\"),\"\",ClassRichIn)","v":""},"ClassRichIn","See above"]
[{"$f":"OF!A8","v":"OF7"},{"$f":"OF!C8","v":"Distance to Nearest Annual Cropland or Developed Land"}," ",null,null,null,{"$f":"IF((Dist2DevCrop=\"\"),\"\",Dist2DevCrop)","v":""},"Dist2DevCrop","Invasive plants that can reduce wetland plant diversity are most prevalent where wetlands or their tributaries are adjoined by agricultural lands and other nutrient sources rather than by forest or other perennial cover (Hychka 2007)."]
[{"$f":"OF!A10","v":"OF9"},{"$f":"OF!C10","v":"Distance to Nearest Well-settled Area"}," ",null,null,null,{"$f":"IF((DistPop=\"\"),\"\",DistPop)","v":""},"DistPop","Non-native plants that can reduce native plant richness tend to be more prevalent closer to population centers because many have been introduced intentionally or unintentionally by humans (Hayden Reichard et al. 2001). "]
[{"$f":"OF!A9","v":"OF8"},{"$f":"OF!C9","v":"Distance to Nearest Road (from Wetland Edge)"}," ",null,null,null,{"$f":"IF((Dist2Road=\"\"),\"\",Dist2Road)","v":""},"Dist2Road","Road corridors are a significant vector for non-native plants that can reduce native plant richness if they invade nearby wetlands. Roads directly promote exotic plant establishment via vehicle dispersal (Schmidt 1989) or disturbance during road construction and maintenance (Safford and Harrison 2001). Roads also promote exotic plant establishment via intentional seeding of soil-stabilizing exotic plants along road verges or in disturbed areas near roads.  Moss and lichen species richness in Alberta woodlands is reduced up to 15m from roads and other woodland edges due to changes in temperature, humidity, and light intensity (Gignac and Dale 2005).  \n"]
[{"$f":"OF!A14","v":"OF13"},{"$f":"OF!C14","v":"% of the Wetland that is Fen Marsh or Swamp"},null,null,null,null,{"$f":"IF((FenMarshSwamp=\"\"),\"\",FenMarshSwamp)","v":""},"FenMarsh Swamp","These wetland classes tend to have greater native plant richness than bogs or open water. "]
[{"$f":"OF!A18","v":"OF17"},{"$f":"OF!C18","v":"Growing Degree Days"}," ",null,null,null,{"$f":"IF((GrowDD=\"\"),\"\",GrowDD)","v":""},"GrowDD","Places with a warmer mean annual temperature may provide opportunity for a greater variety of plant species to colonize substrates that are ice-free for longer during the year."]
[{"$f":"OF!A27","v":"OF26"},{"$f":"OF!C27","v":"Interspersion Index for Internal Herbaceous & Woody Vegetation (macroscale)"}," ",null,null,null,{"$f":"IF((MixHerbWood=\"\"),\"\",MixHerbWood)","v":""},"MixHerbWood","Gaps in woody canopy, or scattered trees and shrubs within a marsh or bog, support a wider variety of plants and indicate a diversity of underlying hydroperiods that have the same effect."]
[{"$f":"OF!A28","v":"OF27"},{"$f":"OF!C28","v":"Interspersion Index for Internal Water & Vegetation (macroscale)"}," ",null,null,null,{"$f":"IF((MixWaterVeg=\"\"),\"\",MixWaterVeg)","v":""},"MixWaterVeg","Greater plant diversity in wetlands is often associated with a well-mixed pattern of water and plants, e.g., the \"hemi-marsh\". This may optimise moisture, nutrients, and sunlight available to wetland plants."]
[{"$f":"OF!A29","v":"OF28"},{"$f":"OF!C29","v":"% Natural Cover within 1km"}," ",null,null,null,{"$f":"IF((NatCov1k=\"\"),\"\",NatCov1k)","v":""},"NatCov1k","Wetlands that are more geographically isolated from each other are likely to have lower plant species richness than those close together (Nekola 1999). Although urbanization typically reduces the diversity of plants in the forest understory, plant community composition in a Wisconsin study was better explained by the amount of surrounding forest than by environmental factors within the studied forests (Rogers et al. 2009). In Ontario, forested wetlands with the most plant species were those with the largest areas and the largest proportion of upland forest within ~ 800 ft of the wetlands (Houlahan et al. 2006). "]
[{"$f":"OF!A31","v":"OF30"},{"$f":"OF!C31","v":"% of AA that is Open Water (macro scale)"},"Inverse",null,null,null,{"$f":"IF((OWpct=\"\"),\"\",1-OWpct)","v":""},"OWpct","Because open water supports fewer plant species than land, a large proportion of open water in a wetland implies lower overall plant richness in most cases, so the scoring uses the inverse."]
[{"$f":"OF!A35","v":"OF34"},{"$f":"OF!C35","v":"% of Wetland Perimeter Adjoined by Natural Cover"}," ",null,null,null,{"$f":"IF((PerimNatCov=\"\"),\"\",PerimNatCov)","v":""},"PerimNatCov","Agricultural and developed land surrounding a wetland contributes invasive plants and pollutants that can reduce native plant richness within a wetland.  Natural cover helps maintain original runoff patterns, microclimate, and water quality."]
[{"$f":"OF!A40","v":"OF39"},{"$f":"OF!C40","v":"Rare Plant Range"},"If wetland is not within range of a rare plant species, then cell is made blank (NULL) and ignored in calculations.",null,null,null,{"$f":"IF((RarePlantRange=\"\"),\"\",IF((RarePlantRange=1),1,\"\"))","v":""},"RarePlantRange","Rare plants contribute disproportionately to regional floristic diversity."]
[{"$f":"OF!A41","v":"OF40"},{"$f":"OF!C41","v":"Road Density in 1km Buffer"},"Inverse",null,null,null,{"$f":"IF((RdDens1k=\"\"),\"\",1-RdDens1k)","v":""},"RdDens1k","See OF8 above."]
[{"$f":"OF!A43","v":"OF42"},{"$f":"OF!C43","v":"Riparian or Floodway Location"}," ",null,null,null,{"$f":"IF((RipFloodpl=\"\"),\"\",RipFloodpl)","v":""},"RipFloodpl","Inflowing streams or rivers bring plant propagules that can sprout and diversify wetland plant communities.  Also, the soil-disturbing and vegetation-thinning effects of natural floods typically diversity plant communities in the long term"]
[{"$f":"OF!A51","v":"OF50"},{"$f":"OF!C51","v":"Springs within 300m"}," ",null,null,null,{"$f":"IF((Spring=\"\"),\"\",Spring)","v":""},"Spring","Several plant species occur almost exclusively in or near springs due to the unique chemistry and thermal regimes of some springs (e.g., Radies et al. 2009)."]
[{"$f":"OF!A57","v":"OF56"},{"$f":"OF!C57","v":"Local Uniqueness of Wetland's Class"}," ",null,null,null,{"$f":"IF((UniqClass=\"\"),\"\",UniqClass)","v":""},"UniqClass","If a particular class is significantly present in a wetland but scarce in the surrounding area, the contribution of its plants to local floristic diversity is likely to be greater."]
[{"$f":"OF!A60","v":"OF59"},{"$f":"OF!C60","v":"Vegetation Connectivity to Other Wetlands within 1 km"}," ",null,null,null,{"$f":"IF((VegCon1k=\"\"),\"\",VegCon1k)","v":""},"VegCon1k","Transport of plant propagules among wetlands by wildlife is probably facilitated if natural vegetation connects the wetlands.  "]
[{"$f":"OF!A64","v":"OF63"},{"$f":"OF!C64","v":"Wetland Density Within 1km"}," ",null,null,null,{"$f":"IF((WetDens1k=\"\"),\"\",WetDens1k)","v":""},"WetDens1k","A greater number of wetlands per unit area implies that any single wetland is likely to be closer to others that can more easily provide propagules for recolonisation if plant communities in the target wetland are altered."]
[{"$f":"OF!A69","v":"OF68"},{"$f":"OF!C69","v":"Wetland Vegetated Area"}," ",null,null,null,{"$f":"IF((WetVegArea=\"\"),\"\",WetVegArea)","v":""},"WetVegArea","Large habitat patches usually support more plant species. Depending on their shape, forest patches sized about 10 acres or larger may provide habitat capable of sustaining a diverse array of bryophyte functional groups (Baldwin & Bradfield 2007). A leveling off of the plant species-area accumulation curve in Alberta forests appeared at a forest patch size of about 27 acres (Gignac & Dale 2007). Blocks of forest smaller than about 9 acres may be less capable of supporting the expected array of mosses in British Columbia (Baldwin & Bradfield 2007), although a study in Washington found that forest patches as small as 2.5 acres, if not narrow, may be large enough to have a microclimate supportive of most plants and animals (Heithecker & Halperin 2007). "]
[{"$f":"OF!A73","v":"OF72"},{"$f":"OF!C73","v":"Surface Water Quality Risk Index"},"Inverse",null,null,null,{"$f":"IF((WQrisk=\"\"),\"\",1-WQrisk)","v":""},"WQrisk","Fertilizers, herbicides, and other pollutants can alter the composition and sometimes the diversity of plants within a wetland, as well as harm pollinating insects."]
["#","Function Indicators from Onsite Visit","Categorical Choices","Data","Weight","Data  x  Weight","Normalised Score","Indicator Abbreviation or Formula","Rationale & Scoring Notes"]
[{"$f":"F!A6","v":"F1"},{"$f":"F!B6","v":"Wetland Type - Predominant"},{"$f":"F!C6","v":"Most of the vegetated part of the AA (wetland Assessment Area) is a (select ONE):"},null,null,null,{"$f":"MAX(F26:F29)/MAX(E26:E29)","v":0},"WettypePD","Fens tend to have richer plant communities than bogs (Thormann & Bayley 1997, Bedford & Godwin 2003, McClellan et al. 2003). Floodplains are exceptionally species-rich (Pollack et al. 1998). Bogs are relatively species-poor, although the species they support tend to be specialized and in some areas may contribute disproportionately to local plant diversity (Moore 1989). Peatlands on slopes tend to be more species-rich than those on flats because contact with enriched groundwater and mineral soils is usually greater."]
[{"$f":"F!A7","v":"F1.1"},null,{"$f":"F!C7","v":"Wooded Swamp"},{"$f":"F!D7","v":0},2,{"$f":"D26*E26","v":0}]
[{"$f":"F!A8","v":"F1.2"},null,{"$f":"F!C8","v":"Bog"},{"$f":"F!D8","v":0},1,{"$f":"D27*E27","v":0}]
[{"$f":"F!A9","v":"F1.3"},null,{"$f":"F!C9","v":"Fen"},{"$f":"F!D9","v":0},4,{"$f":"D28*E28","v":0}]
[{"$f":"F!A10","v":"F1.4"},null,{"$f":"F!C10","v":"Marsh or Shallow Open Water"},{"$f":"F!D10","v":0},5,{"$f":"D29*E29","v":0}]
[{"$f":"F!A11","v":"F2"},{"$f":"F!B11","v":"Wetland Types - Subordinate"},{"$f":"F!C11","v":"Mark all other vegetated wetland types in the AA that occupy more than 1 hectare or more than 1% of the vegetated AA.  Do not mark the predominant type again.  If AA is larger than 1 ha, see preliminary imagery-based answer provided by AESRD, but field-verify."},null,null,null,{"$f":"IF((D35=1),\"\",(1+SUM(D31:D34))/4)","v":0.25},"ClassRichIn15","See above. The score is the number of classes (including one from above) divided by 4."]
[null,null,{"$f":"F!C12","v":"Wooded Swamp"},{"$f":"F!D12","v":0}]
[null,null,{"$f":"F!C13","v":"Bog"},{"$f":"F!D13","v":0}]
[null,null,{"$f":"F!C14","v":"Fen"},{"$f":"F!D14","v":0}]
[null,null,{"$f":"F!C15","v":"Marsh or Shallow Open Water"},{"$f":"F!D15","v":0}]
[null,null,{"$f":"F!C16","v":"no types other than the predominant one in F1 meet the area threshold."},{"$f":"F!D16","v":0}]
[{"$f":"F!A17","v":"F3"},{"$f":"F!B17","v":"% Saturated Only"},{"$f":"F!C17","v":"The percentage of the AA that never contains surface water during an average year (that is, except perhaps for a few hours after snowmelt or rainstorms), but which is still a wetland, is:"},null,null,null,{"$f":"MAX(F37:F42)/MAX(E37:E42)","v":0},"SatPct15","More plant species occur in drier parts of wetlands than in parts that remain flooded for long duration.  However, long duration flooding adds some aquatic species not otherwise found in wetlands."]
[null,null,{"$f":"F!C18","v":"less than 1%, or <0.01 hectare (about 10 m on a side) never has surface water.  In other words, all or nearly all of the AA is inundated permanently or at least seasonally."},{"$f":"F!D18","v":0},1,{"$f":"D37*E37","v":0}]
[null,null,{"$f":"F!C19","v":"1-25% of the AA never contains surface water."},{"$f":"F!D19","v":0},2,0]
[null,null,{"$f":"F!C20","v":"25-50% of the AA never contains surface water."},{"$f":"F!D20","v":0},3,0]
[null,null,{"$f":"F!C21","v":"50-99% of the AA never contains surface water."},{"$f":"F!D21","v":0},4,0]
[null,null,{"$f":"F!C22","v":">99% of the AA never contains surface water, except for water flowing in channels and/or in pools that occupy <1% of the AA. SKIP to F26 (Channel Connection & Outflow Duration)"},{"$f":"F!D22","v":0},3,0]
[null,null,{"$f":"F!C23","v":">99% of the AA never contains surface water, and AA is not intersected by channels that have flow, not even for a few days per year. SKIP to F26."},{"$f":"F!D23","v":0},2,0]
[{"$f":"F!A24","v":"F4"},{"$f":"F!B24","v":"% with Persistent Surface Water"},{"$f":"F!C24","v":"The percentage of the AA that has surface water (either ponded or flowing, either open or obscured by vegetation) during all of the growing season during most years is:"},null,null,null,{"$f":"IF((AllSat+AllSat>0),\"\",MAX(F44:F49)/MAX(E44:E49))","v":0},"PersisPD","Wetlands with less persistent surface water, i.e., more extensive areas that are saturated but lack surface water, or which flood only seasonally, tend to have greater plant species richness.  Wetlands that are entirely covered by persistent water can support only aquatic species, not the full suite of wetland-associated plants.  Disturbance from occasional floods opens the vegetation canopy (Pollack et al. 1998). Seasonal inundation brings in external nutrients to riverine wetlands, and in all wetlands is necessary for seed germination of many wetland plant species. In calculations, is excluded automatically (cell goes blank) if wetland never has surface water during an average year. "]
[null,null,{"$f":"F!C25","v":"less than 1%, or <0.01 hectare (whichever is less).  SKIP to F8 (% Flooded Only Seasonally)."},{"$f":"F!D25","v":0},2,{"$f":"D44*E44","v":0}]
[null,null,{"$f":"F!C26","v":"1-25% of the AA, and mostly in narrow channels and/or small scattered pools."},{"$f":"F!D26","v":0},4,0]
[null,null,{"$f":"F!C27","v":"1-25% of the AA, and mostly in a single large pool, pond, and/or channel."},{"$f":"F!D27","v":0},3,0]
[null,null,{"$f":"F!C28","v":"25-50% of the AA"},{"$f":"F!D28","v":0},2,0]
[null,null,{"$f":"F!C29","v":"50-95% of the AA"},{"$f":"F!D29","v":0},1,0]
[null,null,{"$f":"F!C30","v":">95% of the AA"},{"$f":"F!D30","v":0},0,0]
[{"$f":"F!A45","v":"F9"},{"$f":"F!B45","v":"Annual Water Fluctuation Range"},{"$f":"F!C45","v":"The annual fluctuation in surface water level within most of the parts of the AA that contain surface water is:"},null,null,null,{"$f":"IF((AllSat+AllSat>0),\"\", IF((NoSeasonal=1),\"\",MAX(F51:F54)/MAX(E51:E54)))","v":0},"FlucPD","Wetlands with naturally fluctuating water levels tend to have greater plant species richness (Nicholson 1995, Pollack et al. 1998). Duration, frequency, and timing of inundation may be more important than magnitude of fluctuation, but cannot be estimated during a single visit to an ungaged wetland. Prolonged deep flooding can reduce plant species richness (Bayley & Guimond 2009). In calculations, is excluded automatically (cell goes blank) if wetland never has surface water during an average year, or if none of it floods only seasonally."]
[null,null,{"$f":"F!C46","v":"<10 cm change (stable) "},{"$f":"F!D46","v":0},1,{"$f":"D51*E51","v":0}]
[null,null,{"$f":"F!C47","v":"10 cm - 50 cm change"},{"$f":"F!D47","v":0},2,{"$f":"D52*E52","v":0}]
[null,null,{"$f":"F!C49","v":"1-2 m change"},{"$f":"F!D49","v":0},2,{"$f":"D53*E53","v":0}]
[null,null,{"$f":"F!C50","v":">2 m change"},{"$f":"F!D50","v":0},1,{"$f":"D54*E54","v":0}]
[{"$f":"F!A52","v":"F10"},{"$f":"F!B52","v":"Predominant Depth Class"},{"$f":"F!C52","v":"During most of the time when water is present, its depth in most of the area is: [Note: This is not asking for the maximum depth.]"},null,null,null,{"$f":"IF((AllSat+AllSat>0),\"\", IF((SmallAA=1),\"\", MAX(F56:F60)/MAX(E56:E60)))","v":0},"Depth15","With regard to submersed aquatic plants, shallower areas generally have greater plant richness due to greater availability of light and sediment oxygen. In calculations, is excluded automatically (cell goes blank) if wetland never has surface water during an average year or is <0.01 ha."]
[null,null,{"$f":"F!C53","v":"<10 cm deep (but >0)"},{"$f":"F!D53","v":0},6,{"$f":"D56*E56","v":0}]
[null,null,{"$f":"F!C54","v":"10 - 50 cm deep"},{"$f":"F!D54","v":0},4,{"$f":"D57*E57","v":0}]
[null,null,{"$f":"F!C55","v":"0.5 - 1 m deep"},{"$f":"F!D55","v":0},3,{"$f":"D58*E58","v":0}]
[null,null,{"$f":"F!C56","v":"1 - 2 m deep"},{"$f":"F!D56","v":0},1,{"$f":"D59*E59","v":0}]
[null,null,{"$f":"F!C57","v":">2 m deep.  True for many fringe wetlands."},{"$f":"F!D57","v":0},0,{"$f":"D60*E60","v":0}]
[{"$f":"F!A71","v":"F14"},{"$f":"F!B71","v":"% of Ponded Water That Is Open "},{"$f":"F!C71","v":"In ducks-eye aerial view, the percentage of the ponded water that is open (lacking emergent vegetation during most of the growing season, and unhidden by a forest or shrub canopy) is:"},null,null,null,{"$f":"IF((AllSat+AllSat>0),\"\",IF((OpenW=0),\"\", IF((SmallAA=1),\"\", MAX(F62:F67)/MAX(E62:E67))))","v":""},"PondedOWpct PD","Open water supports fewer plant species than land, so a large proportion of open water in a wetland implies lower overall plant richness in most cases, although at least a little open water is important to support aquatic species. In calculations, is excluded automatically (cell goes blank) if wetland never has surface water during an average year.  Also is excluded automatically if wetland has no ponded water or is <0.01 ha."]
[null,null,{"$f":"F!C72","v":"<1% or none, or largest pool occupies <0.01 hectares.  Enter \"1\" and SKIP to F20 (Floating Algae & Duckweed)."},{"$f":"F!D72","v":0},3,5]
[null,null,{"$f":"F!C73","v":"1-5% of the ponded water.  Enter \"1\" and SKIP to F20."},{"$f":"F!D73","v":0},4,4]
[null,null,{"$f":"F!C74","v":"5-30% of the ponded water."},{"$f":"F!D74","v":0},3,3]
[null,null,{"$f":"F!C75","v":"30-70% of the ponded water."},{"$f":"F!D75","v":0},2,2]
[null,null,{"$f":"F!C76","v":"70-99% of the ponded water."},{"$f":"F!D76","v":0},1,1]
[null,null,{"$f":"F!C77","v":"100% of the ponded water. "},{"$f":"F!D77","v":0},0,0]
[{"$f":"F!A84","v":"F16"},{"$f":"F!B84","v":"Predominant Width of Vegetated Zone within Wetland"},{"$f":"F!C84","v":"At the driest time of year (or lowest water level), the average width of vegetated area in the AA that separates adjoining uplands from open water within the AA is:"},null,null,null,{"$f":"IF((AllSat+AllSat>0),\"\",IF((OpenW=0),\"\", IF((SmallAA=1),\"\", MAX(F69:F73)/MAX(E69:E73))))","v":""},"WidthPD","Wetlands with wider vegetated areas are more likely to contain more plant species and rarer and more sensitive plants, as well as being more insulated from some upland disturbances (Rooney & Bayley 2011). In calculations, is excluded automatically (cell goes blank) if wetland never has surface water during an average year or if wetland lacks open water or is <0.01 ha."]
[null,null,{"$f":"F!C85","v":"<1 m"},{"$f":"F!D85","v":0},1,{"$f":"D69*E69","v":0}]
[null,null,{"$f":"F!C86","v":"1 - 9 m"},{"$f":"F!D86","v":0},2,{"$f":"D70*E70","v":0}]
[null,null,{"$f":"F!C87","v":"10 - 29 m"},{"$f":"F!D87","v":0},3,{"$f":"D71*E71","v":0}]
[null,null,{"$f":"F!C88","v":"30 - 49 m"},{"$f":"F!D88","v":0},4,{"$f":"D72*E72","v":0}]
[null,null,{"$f":"F!C90","v":"> 100 m"},{"$f":"F!D90","v":0},5,{"$f":"D73*E73","v":0}]
[{"$f":"F!A95","v":"F18"},{"$f":"F!B95","v":"Interspersion of Robust Emergents & Open Water"},{"$f":"F!C95","v":"During most of the growing season, the spatial pattern of tall robust herbaceous vegetation (e.g., cattail, bulrush) that has surface water beneath it is mostly:"},null,null,null,{"$f":"IF((AllSat+AllSat>0),\"\",IF((NoPonded=1),\"\",IF((NoOpenPonded+NoOpenPonded1>0),\"\",IF((AllOpenPond=1),\"\", IF((SmallAA=1),\"\", MAX(F75:F77)/MAX(E75:E77))))))","v":0},"InterspersPD","Greater plant diversity in wetlands is often associated with a well-mixed pattern of water and plants, e.g., the \"hemi-marsh\". This may optimise moisture, nutrients, and sunlight available to wetland plants.  Relatively even mixes of emergent plants and open water also imply that both submerged aquatics and emergents may be present, thus comprising greater diversity. In calculations, is excluded automatically (cell goes blank) if wetland never has surface water during an average year, if no ponded water, if ponded water but no vegetation, if ponded but no open water, or if <0.01 ha."]
[null,null,{"$f":"F!C96","v":"Scattered in small clumps, islands, or patches throughout the surface water area."},{"$f":"F!D96","v":0},3,{"$f":"D75*E75","v":0}]
[null,null,{"$f":"F!C97","v":"Intermediate"},{"$f":"F!D97","v":0},2,{"$f":"D76*E76","v":0}]
[null,null,{"$f":"F!C98","v":"Clumped at one or a few sides of the surface water area, or mostly surrounds a central area of open water.  Or such vegetation is absent or covers <9 sq m and <1% of the AA."},{"$f":"F!D98","v":0},1,{"$f":"D77*E77","v":0}]
[{"$f":"F!A103","v":"F23"},{"$f":"F!B103","v":"Beaver Probability"},{"$f":"F!C103","v":"Use of the AA by beaver during the past 5 years is (select most applicable ONE):"},null,null,null,{"$f":"IF((AllSat+AllSat>0),\"\",MAX(F79:F82)/MAX(E79:E82))","v":0},"BeaverPD","Beaver impoundments increase richness of wetland plants locally, especially a few years after they are abandoned (Pollock et al. 1998, Wright et al. 2002, 2003; Bayley & Guimond 2008, Hood & Bayley 2008). In calculations, is excluded automatically (cell goes blank) if wetland never has surface water during an average year."]
[null,null,{"$f":"F!C104","v":"evident from direct observation or presence of gnawed limbs, dams, tracks, dens, lodges, or extensive stands of water-killed trees (snags)."},{"$f":"F!D104","v":0},5,{"$f":"D79*E79","v":0}]
[null,null,{"$f":"F!C105","v":"likely based on known occurrence in the region and proximity to suitable habitat, which may include: (a) a persistent freshwater wetland, pond, or lake, or a perennial low or mid-gradient (<10%) channel, and (b) a corridor or multiple stands of hardwood trees and shrubs in vegetated areas near surface water."},{"$f":"F!D105","v":0},2,{"$f":"D80*E80","v":0}]
[null,null,{"$f":"F!C106","v":"unlikely because site characteristics above are deficient, and/or this is a settled area or other area where beaver are routinely removed.  But beaver occur in this part of the region (i.e., within 25 km)."},{"$f":"F!D106","v":0},1,{"$f":"D81*E81","v":0}]
[null,null,{"$f":"F!C107","v":"none.  Beaver are absent from this part of the region."},{"$f":"F!D107","v":0},0,{"$f":"D82*E82","v":0}]
[{"$f":"F!A108","v":"F24"},{"$f":"F!B108","v":"Inflow"},{"$f":"F!C108","v":"At least once annually, surface water from a tributary >100m long, or from a larger permanent water body, moves into the AA. It may enter directly in a channel, or as unconfined overflow from a contiguous river or lake, or via a pipe or hardened conduit.   If true, enter 1 and continue.  If false, enter 0 and SKIP to F26 (Channel Connection & Outflow Duration)."},{"$f":"Inflows","v":0},null,null,{"$f":"D83","v":0},"InfloPD","Inflowing streams bring plant propagules that can sprout and diversify wetland plant communities."]
[{"$f":"F!A125","v":"F28"},{"$f":"F!B125","v":"Groundwater: Strength of Evidence"},{"$f":"F!C125","v":"Select first applicable choice. "},null,null,null,{"$f":"IF((D87=1),\"\",MAX(F85:F87)/MAX(E85:E87))","v":0},"GWpd","Partly because of the greater nutrient levels and hydrologic stability of most groundwater, several plant species thrive best where a wetland's surface water originates most directly from groundwater (e.g., Radies et al. 2009). In calculations, is excluded automatically (cell goes blank) if no evidence of groundwater influx; otherwise is rated based on response in column D."]
[null,null,{"$f":"F!C126","v":"Groundwater monitoring has demonstrated that groundwater primarily discharges to the wetland for longer periods during the year than periods when the wetland recharges the groundwater.  Or, springs are known to be present within the AA.\n\n\n"},{"$f":"F!D126","v":0},2,{"$f":"D85*E85","v":0}]
[null,null,{"$f":"F!C127","v":"One or more of the following are true: (a) the upper end of the AA is located very close to the base of (but mostly not ON) a natural slope much steeper (usually >15%) than that within the AA and longer than 100 m, OR\n(b) rust deposits (\"iron floc\"), colored precipitates, or dispersible natural oil sheen are prevalent in the AA, OR\n(c) AA water is remarkably clear in contrast to naturally stained waters typical in nearby wetlands, OR\n(d) AA is located at a geologic fault.\n\n"},{"$f":"F!D127","v":0},1,{"$f":"D86*E86","v":0}]
[null,null,{"$f":"F!C128","v":"Neither of above is true, although some groundwater may discharge to or flow through the AA.  Or groundwater influx is unknown."},{"$f":"F!D128","v":0},0,{"$f":"D87*E87","v":0}]
[{"$f":"F!A134","v":"F30"},{"$f":"F!B134","v":"Total Woody Cover -% of the Vegetated AA"},{"$f":"F!C134","v":"Within the entire vegetated part of the AA, the percentage occupied by trees or shrubs taller than 1 m is:"},null,null,null,{"$f":"MAX(F89:F93)/MAX(E89:E93)","v":0},"WoodyCovPD","At least a small amount of woody cover enhances plant diversity within a wetland, but more often, too much implies that shading of the understory by a woody plant canopy will limit the diversity of herbaceous plants."]
[null,null,{"$f":"F!C135","v":"<5% of the vegetated AA, or there is no woody vegetation in the AA.  SKIP to F38 (N Fixers)"},{"$f":"F!D135","v":0},2,{"$f":"D89*E89","v":0}]
[null,null,{"$f":"F!C136","v":"5-25%.  "},{"$f":"F!D136","v":0},5,0]
[null,null,{"$f":"F!C137","v":"25-50%"},{"$f":"F!D137","v":0},4,0]
[null,null,{"$f":"F!C138","v":"50-75%"},{"$f":"F!D138","v":0},3,0]
[null,null,{"$f":"F!C139","v":">75%"},{"$f":"F!D139","v":0},1,0]
[{"$f":"F!A140","v":"F31"},{"$f":"F!B140","v":"Interspersion of Herbaceous and Woody Cover"},{"$f":"F!C140","v":"The following best represents the distribution pattern of woody vegetation VS. unshaded herbaceous/ moss vegetation within the AA:"},null,null,null,{"$f":"MAX(F95:F98)/MAX(E95:E98)","v":0},"HerbWood15","Gaps in woody canopy, or scattered trees and shrubs within a marsh or bog, support a wider variety of plants and indicate a diversity of underlying hydroperiods that have the same effect."]
[null,null,{"$f":"F!C141","v":"(a) Woody cover and herbaceous/ moss cover EACH comprise 30-70% of the vegetated part of the AA, AND (b) There are many patches of woody vegetation scattered widely within herbaceous/ moss vegetation, or many patches of herbaceous vegetation scattered widely within woody vegetation."},{"$f":"F!D141","v":0},3,0]
[null,null,{"$f":"F!C142","v":"(a) Woody cover and herbaceous/ moss EACH comprise 30-70% of the vegetated AA, AND (b) There are few patches (\"islands\") of woody vegetation scattered widely within herbaceous vegetation, or few patches of herbaceous/ moss vegetation (\"gaps\") scattered widely within woody vegetation."},{"$f":"F!D142","v":0},2,0]
[null,null,{"$f":"F!C143","v":"(a) Woody cover OR herbaceous/ moss comprise >70% of the vegetated AA, AND (b) There are several patches of the other scattered within it. "},{"$f":"F!D143","v":0},1,0]
[null,null,{"$f":"F!C144","v":"(a) Woody cover OR herbaceous/ moss comprise >70% of the vegetated AA, AND (b) The other is absent or is mostly in a single area or distinct zone with almost no intermixing of woody and unshaded herbaceous/ moss vegetation."},{"$f":"F!D144","v":0},0,0]
[{"$f":"F!A145","v":"F32"},{"$f":"F!B145","v":"Tall Woody Canopy- % of the Vegetated AA"},{"$f":"F!C145","v":"Within the vegetated part of the AA, just the woody plants taller than 3 m occupy:"},null,null,null,{"$f":"IF((NoWoodyVeg=1),\"\", MAX(F100:F104)/MAX(E100:E104))","v":0},"TreeCovPD","Plant diversity is often greater without the shading and nutrient-competitive effects of trees (Hanley & Brady 1997).  Intermediate levels of canopy closure usually support the most plant species (e.g., Halpern & Spies 1995, Chavez & Macdonald 2010, Chipman & Johnson 2002).  In calculations, is excluded automatically (cell goes blank) if woody vegetation is <5% of the vegetated part of the AA."]
[null,null,{"$f":"F!C146","v":"<1% of the vegetated AA, or the AA lacks trees.  Enter \"1\" and SKIP to F35 (Exposed Shrub)."},{"$f":"F!D146","v":0},1,{"$f":"D100*E100","v":0}]
[null,null,{"$f":"F!C147","v":"1-25% of the vegetated AA"},{"$f":"F!D147","v":0},2,{"$f":"D101*E101","v":0}]
[null,null,{"$f":"F!C148","v":"25-50% of the vegetated AA"},{"$f":"F!D148","v":0},3,{"$f":"D102*E102","v":0}]
[null,null,{"$f":"F!C149","v":"50-95% of the vegetated AA"},{"$f":"F!D149","v":0},2,{"$f":"D103*E103","v":0}]
[null,null,{"$f":"F!C150","v":">95% of the vegetated part of the AA"},{"$f":"F!D150","v":0},0,{"$f":"D104*E104","v":0}]
[{"$f":"F!A151","v":"F33"},{"$f":"F!B151","v":"Woody Diameter Classes"},{"$f":"F!C151","v":"Mark all the classes of woody plants within the AA, but only IF they comprise more than 5% of the woody canopy within the AA.  Do not count trees that adjoin but are not within the AA."},null,null,null,{"$f":"IF((NoWoodyVeg=1),\"\",IF((NoTrees=1),\"\",((SUM(D106:D113)/8+ MAX(F106:F113)/MAX(E106:E113))/2)))","v":0},"dbhPD","Deciduous forests, because of their less acidic soils and more open canopies, often support greater plant richness than coniferous forests.  Larger-diameter stands sometime indicate more mature soils which support more native plant species than younger stands with comparable light conditions. In calculations, is excluded automatically (cell goes blank) if trees occupy <5% of the vegetated part of the AA. Otherwise, score is based on the number of categories and a weighted average that favors larger deciduous trees."]
[null,null,{"$f":"F!C152","v":"coniferous, 1-9 cm diameter and >1 m tall"},{"$f":"F!D152","v":0},1,{"$f":"D106*E106","v":0}]
[null,null,{"$f":"F!C153","v":"broad-leaved deciduous 1-9 cm diameter and >1 m tall"},{"$f":"F!D153","v":0},3,0]
[null,null,{"$f":"F!C154","v":"coniferous, 10-19 cm diameter"},{"$f":"F!D154","v":0},2,0]
[null,null,{"$f":"F!C155","v":"broad-leaved deciduous 10-19 cm diameter"},{"$f":"F!D155","v":0},4,0]
[null,null,{"$f":"F!C156","v":"coniferous, 20-40 cm diameter"},{"$f":"F!D156","v":0},3,0]
[null,null,{"$f":"F!C157","v":"broad-leaved deciduous 20-40 cm diameter"},{"$f":"F!D157","v":0},6,0]
[null,null,{"$f":"F!C158","v":"coniferous, >40 cm diameter"},{"$f":"F!D158","v":0},5,0]
[null,null,{"$f":"F!C159","v":"broad-leaved deciduous >40 cm diameter"},{"$f":"F!D159","v":0},8,0]
[{"$f":"F!A160","v":"F34"},{"$f":"F!B160","v":"Downed Wood"},{"$f":"F!C160","v":"The number of downed wood pieces longer than 2 m and with diameter >10 cm, and not persistently submerged, is:"},null,null,null,{"$f":"IF((NoWoodyVeg=1),\"\", IF((NoShrub=1),\"\", MAX(F115:F116)))","v":0},"DownWood15","Downed wood adds microtopographic relief to wetlands and can serve as \"nurse logs\" that allow many plants to germinate with less competition or exposure to prolonged inundation.  This may increase plant richness within a site. Downed wood also provides nest or dormancy sites for many insect pollinators. In calculations, is excluded automatically (cell goes blank) if woody vegetation is <5% of the vegetated part of the AA."]
[null,null,{"$f":"F!C161","v":"Several ( >5 if AA is >5 hectares, less for smaller AAs)"},{"$f":"F!D161","v":0},1,0]
[null,null,{"$f":"F!C162","v":"Few or none "},{"$f":"F!D162","v":0},0,0]
[{"$f":"F!A163","v":"F35"},{"$f":"F!B163","v":"Exposed Shrub Canopy"},{"$f":"F!C163","v":"Woody vegetation 1 to 3 m tall that is not under the drip line of taller woody vegetation comprises:"},null,null,null,{"$f":"IF((NoWoodyVeg=1),\"\", MAX(F118:F122)/MAX(E118:E122))","v":0},"ShrubSun","Shrubs contribute to onsite plant diversity, but are generally less diverse than herbaceous plants, which are often more diverse without the shading and nutrient-competitive effects of shrubs. Sparse shrub cover sometimes indicates overgrazing by deer, which reduces plant diversity. Damages to native ecosystems from abnormally high deer density have been documented on an island in British Columbia (Allombert et al. 2005). Such damage to shrubs and ground cover occurs in places where fragmentation of forests has created deer densities of more than about 1 per 25 acres (Thiemann et al. 2009, Martin et al. 2010).  In calculations, is excluded automatically (cell goes blank) if woody vegetation is <5% of the vegetated part of the AA."]
[null,null,{"$f":"F!C164","v":"<5% of the vegetated AA and (if a fringe wetland) <5% of its water edge.  Or <0.01 hectare.  SKIP to F38 (N Fixers)."},{"$f":"F!D164","v":0},1,{"$f":"D118*E118","v":0}]
[null,null,{"$f":"F!C165","v":"5-25% of the vegetated AA or (if a fringe wetland) 5-25% of the water edge  -- whichever is greater."},{"$f":"F!D165","v":0},3,{"$f":"D119*E119","v":0}]
[null,null,{"$f":"F!C166","v":"25-50% of the vegetated AA or the water edge, whichever is greater. "},{"$f":"F!D166","v":0},2,{"$f":"D120*E120","v":0}]
[null,null,{"$f":"F!C167","v":"50-95% of the vegetated AA or the water edge, whichever is greater."},{"$f":"F!D167","v":0},1,{"$f":"D121*E121","v":0}]
[null,null,{"$f":"F!C168","v":">95% of the vegetated part of the AA or the water edge, whichever is greater."},{"$f":"F!D168","v":0},0,{"$f":"D122*E122","v":0}]
[{"$f":"F!A169","v":"F36"},{"$f":"F!B169","v":"Dominance of Most Abundant Shrub Species "},{"$f":"F!C169","v":"Determine which two native shrub species (1 to 3 m tall) comprise the greatest portion of the native shrub cover.  Then choose one of the following:"},null,null,null,{"$f":"IF((NoWoodyVeg=1),\"\", IF((NoShrub=1),\"\", MAX(F124:F125)))","v":0},"wood2pd","A dominance of common species usually implies overall reduction in plant species richness. In calculations, is excluded automatically (cell goes blank) if exposed shrub cover is <5% of the vegetated part of the AA."]
[null,null,{"$f":"F!C170","v":"those species together comprise > 50% of the areal cover of native shrub species."},{"$f":"F!D170","v":0},0,{"$f":"D124*E124","v":0}]
[null,null,{"$f":"F!C171","v":"those species together do not comprise > 50% of the areal cover of native shrub species."},{"$f":"F!D171","v":0},1,{"$f":"D125*E125","v":0}]
[{"$f":"F!A172","v":"F37"},{"$f":"F!B172","v":"Broad-leaved Deciduous Trees and Shrubs"},{"$f":"F!C172","v":"The percentage of the AA's tree or shrub cover that is broad-leaved deciduous and is taller than 1 meter is:"},null,null,null,{"$f":"IF((NoWoodyVeg=1),\"\",MAX(F127:F131)/MAX(E127:E131))","v":0},"HardwdPD","Dominance by deciduous cover allows more light to penetrate to the ground.  In many instances this results in greater richness of understory plant species. In calculations, is excluded automatically (cell goes blank) if woody vegetation is <5% of the vegetated part of the AA."]
[null,null,{"$f":"F!C173","v":"<1%, or largest patch occupies less than 0.01 hectare"},{"$f":"F!D173","v":0},0,{"$f":"D127*E127","v":0}]
[null,null,{"$f":"F!C174","v":"1-25% of the tree or shrub cover (whichever has more)"},{"$f":"F!D174","v":0},1,{"$f":"D128*E128","v":0}]
[null,null,{"$f":"F!C175","v":"25-50% of the tree or shrub cover (whichever has more)"},{"$f":"F!D175","v":0},2,{"$f":"D129*E129","v":0}]
[null,null,{"$f":"F!C176","v":"50-75% of the tree or shrub cover (whichever has more)"},{"$f":"F!D176","v":0},3,{"$f":"D130*E130","v":0}]
[null,null,{"$f":"F!C177","v":">75% of the tree or shrub cover (whichever has more)"},{"$f":"F!D177","v":0},2,{"$f":"D131*E131","v":0}]
[{"$f":"F!A178","v":"F38"},{"$f":"F!B178","v":"N Fixers"},{"$f":"F!C178","v":"The percent of the AA's shrub plus ground cover that is nitrogen-fixing plants (e.g., alder, baltic (wire) rush, sweetgale, lupine, clover, other legumes) is:"},null,null,null,{"$f":"MAX(F133:F137)/MAX(E133:E137)","v":0},"NfixPD","Alder often occurs in mildly disturbed settings, and through its ability to increase soil fertility by fixing nitrogen, can increase the diversity and abundance of understory plants (Deal 1997). However, as alder stands age, they form a closed canopy which can block light and reduce understory plant richness."]
[null,null,{"$f":"F!C179","v":"<1% or none"},{"$f":"F!D179","v":0},0,{"$f":"D133*E133","v":0}]
[null,null,{"$f":"F!C180","v":"1-25% of the shrub plus ground cover, in the AA or along its water edge (whichever has more)."},{"$f":"F!D180","v":0},2,{"$f":"D134*E134","v":0}]
[null,null,{"$f":"F!C181","v":"25-50% of the shrub plus ground cover, in the AA or along its water edge (whichever has more)."},{"$f":"F!D181","v":0},3,{"$f":"D135*E135","v":0}]
[null,null,{"$f":"F!C182","v":"50-75% of the shrub plus ground cover, in the AA or along its water edge (whichever has more)."},{"$f":"F!D182","v":0},2,{"$f":"D136*E136","v":0}]
[null,null,{"$f":"F!C183","v":">75% of the shrub plus ground cover, in the AA or along its water edge (whichever has more)."},{"$f":"F!D183","v":0},1,{"$f":"D137*E137","v":0}]
[{"$f":"F!A184","v":"F39"},{"$f":"F!B184","v":"Snags"},{"$f":"F!C184","v":"The number of large snags (diameter >20 cm) in the AA plus the upland area within 10 m of the wetland edge is:"},null,null,null,{"$f":"IF((NoWoodyVeg=1),\"\", IF((NoShrub=1),\"\", MAX(F139:F141)))","v":0},"Snags15","Snags provide nest or dormancy sites for many insect pollinators. The removal of dead wood, which often accompanies lakeshore development, has been associated with reduced pollination (Trant et al. 2010)."]
[null,null,{"$f":"F!C185","v":"Several ( >2/hectare) and a pond, lake, or slow-flowing water wider than 10 m is within 1 km."},{"$f":"F!D185","v":0},1,{"$f":"D139*E139","v":0}]
[null,null,{"$f":"F!C186","v":"Several ( >2/hectare) but above not true."},{"$f":"F!D186","v":0},1,0]
[null,null,{"$f":"F!C187","v":"Few or none "},{"$f":"F!D187","v":0},0,0]
[{"$f":"F!A188","v":"F40"},{"$f":"F!B188","v":"Moss Extent"},{"$f":"F!C188","v":"Within the part of the AA that lacks persistent surface water, the cover of moss is:"},null,null,null,{"$f":"IF((AllWet=1),\"\",MAX(F143:F147)/MAX(E143:E147))","v":0},"MossPD","Moss usually indicates acidic conditions that generally support fewer plant species. Acidifying Sphagnum mosses, which inhibit the expansion of diverse communities of vascular plants, tend to decline above a pH of 5.5 (Vitt 2006). By acidifying the soil, Sphagnum moss slows down decomposition and thus the availability of nutrients for other plants (Malmer et al. 2003). Although plant richness is usually less in moss wetlands compared to others, the species that occur are often specialized and regionally uncommon. In calculations, is excluded automatically (cell goes blank) if the site contains virtually no wetland vegetation."]
[null,null,{"$f":"F!C189","v":"<5% of the ground cover"},{"$f":"F!D189","v":0},4,{"$f":"D143*E143","v":0}]
[null,null,{"$f":"F!C190","v":"5-25% of the ground cover"},{"$f":"F!D190","v":0},5,{"$f":"D144*E144","v":0}]
[null,null,{"$f":"F!C191","v":"25-50% of the ground cover"},{"$f":"F!D191","v":0},3,{"$f":"D145*E145","v":0}]
[null,null,{"$f":"F!C192","v":"50-95% of the ground cover"},{"$f":"F!D192","v":0},2,{"$f":"D146*E146","v":0}]
[null,null,{"$f":"F!C193","v":">95% of the ground cover"},{"$f":"F!D193","v":0},1,{"$f":"D147*E147","v":0}]
[{"$f":"F!A200","v":"F42"},{"$f":"F!B200","v":"Ground Irregularity"},{"$f":"F!C200","v":"Consider the parts of the AA that lack surface water at some time of the year.  Excluding slash from logging, the number of small pits, raised mounds, hummocks, boulders, upturned trees, animal burrows, gullies, natural levees, wide soil cracks, and microdepressions is:"},null,null,null,{"$f":"MAX(F149:F151)/MAX(E149:E151)","v":0},"GirregPD","Different plant species occur under different moisture regimes, which correlate with different elevations (Samoni et al. 2010), so a greater diversity of elevations (i.e., complex microtopography) often supports a wider variety of wetland plants (Benscoter & Vitt 2008). Adding small ridges and furrows to constructed depressional wetlands was found in one study to increase their percent cover of obligate wetland species (Alsfeld et al. 2009). Wetlands with more varied topography (e.g., more hummocks) tend to have greater plant species richness because this created different flood frequencies within the wetland (Pollack et al. 1998)."]
[null,null,{"$f":"F!C201","v":"Few or none (minimal microtopography; <1% of that area) "},{"$f":"F!D201","v":0},0,{"$f":"D149*E149","v":0}]
[null,null,{"$f":"F!C202","v":"Intermediate"},{"$f":"F!D202","v":0},1,{"$f":"D150*E150","v":0}]
[null,null,{"$f":"F!C203","v":"Several (extensive micro-topography)"},{"$f":"F!D203","v":0},2,{"$f":"D151*E151","v":0}]
[{"$f":"F!A208","v":"F44"},{"$f":"F!B208","v":"Soil Texture"},{"$f":"F!C208","v":"In parts of the AA that lack persistent water, the texture of soil in the uppermost layer is mostly:  [To determine this, use a trowel to check in at least 3 widely spaced locations, and use the soil texture key in Appendix A of the Manual]"},null,null,null,{"$f":"MAX(F153:F156)/MAX(E153:E156)","v":0},"SoilTexPD","Coarse soils tend to be less productive and in some cases this results in reduced species richness of wetland plants. Wetland soils with higher organic content often support greater plant species richness (e.g., Alsfeld et al. 2009) but only if not too acidic (e.g., fens are not). However, when organic soils are acidic (e.g., bogs) they often support species uncommon in wetlands elsewhere."]
[null,null,{"$f":"F!C209","v":"Loamy: includes loam, sandy loam"},{"$f":"F!D209","v":0},3,{"$f":"D153*E153","v":0}]
[null,null,{"$f":"F!C210","v":"Fines: includes silt, glacial flour, clay, clay loam, silty clay, silty clay loam, sandy clay, sandy clay loam."},{"$f":"F!D210","v":0},2,{"$f":"D154*E154","v":0}]
[null,null,{"$f":"F!C211","v":"Organic"},{"$f":"F!D211","v":0},3,{"$f":"D155*E155","v":0}]
[null,null,{"$f":"F!C212","v":"Coarse: includes sand, loamy sand, gravel, cobble, stones, boulders, fluvents, fluvaquents, riverwash."},{"$f":"F!D212","v":0},0,{"$f":"D156*E156","v":0}]
[{"$f":"F!A224","v":"F47"},{"$f":"F!B224","v":"Forb Cover"},{"$f":"F!C224","v":"The areal cover of forbs reaches an annual maximum of:"},null,null,null,{"$f":"IF((NoHerbCov=1),\"\",MAX(F158:F162)/MAX(E158:E162))","v":0},"forbsPD","As a group, forbs tend to be more diverse than graminoids and thus contribute significantly to biodiversity within and among wetlands. In calculations, is excluded automatically (cell goes blank) if herbaceous cover is <5% of the vegetated cover."]
[null,null,{"$f":"F!C225","v":"<5% of the herbaceous & moss cover"},{"$f":"F!D225","v":0},0,{"$f":"D158*E158","v":0}]
[null,null,{"$f":"F!C226","v":"5-25% of the herbaceous & moss cover"},{"$f":"F!D226","v":0},3,0]
[null,null,{"$f":"F!C227","v":"25-50% of the herbaceous & moss cover"},{"$f":"F!D227","v":0},4,0]
[null,null,{"$f":"F!C228","v":"50-95% of the herbaceous & moss cover"},{"$f":"F!D228","v":0},2,0]
[null,null,{"$f":"F!C229","v":">95% of the herbaceous & moss cover. SKIP to F50 (Invasive Plant Cover)."},{"$f":"F!D229","v":0},1,0]
[{"$f":"F!A230","v":"F48"},{"$f":"F!B230","v":"Sedge Cover"},{"$f":"F!C230","v":"Sedges (Carex spp.) and/or cottongrass (Eriophorum spp.) occupy:"},null,null,null,{"$f":"IF((NoHerbCov=1),\"\", MAX(F164:F167)/MAX(E164:E167))","v":0},"sedgePD","As a group, sedges tend to be extremely diverse and thus contribute significantly to biodiversity within and among wetlands.  They also are often associated with diverse assemblages of other plants because they tend to occur in wetlands with the fewest previous disturbances and/or pollution. In calculations, is excluded automatically (cell goes blank) if herbaceous cover is <5% of the vegetated cover."]
[null,null,{"$f":"F!C231","v":"<5% of the herbaceous cover, or <0.01 hectare"},{"$f":"F!D231","v":0},0,0]
[null,null,{"$f":"F!C232","v":"5-50% of the herbaceous cover"},{"$f":"F!D232","v":0},3,0]
[null,null,{"$f":"F!C233","v":"50-95% of the herbaceous cover"},{"$f":"F!D233","v":0},2,0]
[null,null,{"$f":"F!C234","v":">95% of the herbaceous cover"},{"$f":"F!D234","v":0},1,0]
[{"$f":"F!A235","v":"F49"},{"$f":"F!B235","v":"Dominance of Most Abundant Herbaceous Species "},{"$f":"F!C235","v":"Determine which two native herbaceous (forb and graminoid) species comprise the greatest portion of the herbaceous cover that is unshaded by a woody canopy.  Then choose one of the following:"},null,null,null,{"$f":"IF((NoHerbCov=1),\"\", MAX(F169:F170))","v":0},"herbdom15","Wetlands not dominated a one or two plant species are, by definition, more diverse. Included in calculations only if herbaceous cover is >5% of vegetated cover and second choice is answered positively."]
[null,null,{"$f":"F!C236","v":"those species together comprise > 50% of the areal cover of native herbaceous plants at any time during the year."},{"$f":"F!D236","v":0},0,{"$f":"D169*E169","v":0}]
[null,null,{"$f":"F!C237","v":"those species together do not comprise > 50% of the areal cover of native herbaceous plants at any time during the year."},{"$f":"F!D237","v":0},1,{"$f":"D170*E170","v":0}]
[{"$f":"F!A238","v":"F50"},{"$f":"F!B238","v":"Invasive Plant Cover"},{"$f":"F!C238","v":"In central Alberta, common invasive graminoids include smooth brome, most bluegrasses, quackgrass, timothy, alfalfa, reed canarygrass, red fescue, spreading bentgrass.  Common invasive forbs include most thistles and sow-thistles, most clovers, sweetclover, black medick, dandelion, great plantain, hemp-nettle, lamb's-quarters, shepherd's-purse, curly dock, pennycress, wallflower, hawksbeard, tansy, chickweed, sticky-willy bedstraw, stickseed, tall buttercup. Select first applicable choice:"},null,null,null,{"$f":"MAX(F172:F176)/MAX(E172:E176)","v":0},"Invasives","Invasion by non-native species typically results in a reduction in native plant species richness. In some regions, a change of only 4 inches in mean water level or a change of only 1 inch in the degree of fluctuation may cause a shift from native to non-native species (Magee & Kentula 2005)."]
[null,null,{"$f":"F!C239","v":"invasive or other non-native species appear to be absent in the AA, or are present only in trace amount (a few individuals)"},{"$f":"F!D239","v":0},4,{"$f":"D172*E172","v":0}," "]
[null,null,{"$f":"F!C240","v":"Invasive species are present in more than trace amounts, but comprise <5% of herbaceous cover (or woody cover, if the invasives are woody)."},{"$f":"F!D240","v":0},3,{"$f":"D173*E173","v":0}]
[null,null,{"$f":"F!C241","v":"Invasive species comprise 5-20% of the herb cover."},{"$f":"F!D241","v":0},2,{"$f":"D174*E174","v":0}]
[null,null,{"$f":"F!C242","v":"Invasive species comprise 20-50% of the herb cover."},{"$f":"F!D242","v":0},1,{"$f":"D175*E175","v":0}]
[null,null,{"$f":"F!C243","v":"Invasive species comprise >50% of the herb cover."},{"$f":"F!D243","v":0},0,{"$f":"D176*E176","v":0}]
[{"$f":"F!A244","v":"F51"},{"$f":"F!B244","v":"Weed Source Along Edge"},{"$f":"F!C244","v":"Along the wetland-upland boundary, the percent of the upland edge (within 3 m of wetland) that is occupied by plant species that are considered invasive (see above) is:"},null,null,null,{"$f":"MAX(F178:F181)/MAX(E178:E181)","v":0},"WeedSourcePD","Although not all invasive upland plants are capable of establishing sustained populations in wetlands, many can. When they do they reduce plant diversity."]
[null,null,{"$f":"F!C245","v":"none of the upland edge (invasives apparently absent)"},{"$f":"F!D245","v":0},4,{"$f":"D178*E178","v":0}]
[null,null,{"$f":"F!C246","v":"some (but <5%) of the upland edge"},{"$f":"F!D246","v":0},3,{"$f":"D179*E179","v":0}]
[null,null,{"$f":"F!C247","v":"5-50% of the upland edge"},{"$f":"F!D247","v":0},2,{"$f":"D180*E180","v":0}]
[null,null,{"$f":"F!C248","v":"most (>50%) of the upland edge"},{"$f":"F!D248","v":0},0,{"$f":"D181*E181","v":0}]
[{"$f":"F!A249","v":"F52"},{"$f":"F!B249","v":"Natural Cover in Buffer"},{"$f":"F!C249","v":"Along the wetland-upland edge and extending 30 m upslope, the percentage of the upland that contains natural (not necessarily native -- see column E) land cover taller than 10 cm is:"},null,null,null,{"$f":"MAX(F183:F187)/MAX(E183:E187)","v":0},"NatVegCApd","Lichens and mosses have been affected by edge-induced microclimate changes extending at least 50 ft into forested areas (Hylander et al. 2002, Boudreault et al. 2008) and as far as ~150 ft from the forest edge (Baldwin & Bradfield 2005). In Oregon, selective thinning of forests that adjoined riparian buffers did not affect the herbaceous or shrub cover in the buffers when they were wider than ~50 ft (Anderson & Meleason 2009). Thinning can increase the distance seeds disperse into the forest and the number that disperse successfully (Cadenasso et al. 2001). One study found that where more than 50% of the basal area was cut, a significantly different plant community structure resulted (Deal 2001). "]
[null,null,{"$f":"F!C250","v":"<5% "},{"$f":"F!D250","v":0},0,{"$f":"D183*E183","v":0}]
[null,null,{"$f":"F!C251","v":"5 to 30%"},{"$f":"F!D251","v":0},2,{"$f":"D184*E184","v":0}]
[null,null,{"$f":"F!C252","v":"30 to 60%"},{"$f":"F!D252","v":0},3,{"$f":"D185*E185","v":0}]
[null,null,{"$f":"F!C253","v":"60 to 90%"},{"$f":"F!D253","v":0},4,{"$f":"D186*E186","v":0}]
[null,null,{"$f":"F!C254","v":">90%.  SKIP to F54 (Cliffs)."},{"$f":"F!D254","v":0},6,{"$f":"D187*E187","v":0}]
[{"$f":"F!A255","v":"F53"},{"$f":"F!B255","v":"Type of Cover in Buffer"},{"$f":"F!C255","v":"Within 30 m upslope of the wetland-upland edge closest to the AA, the upland land cover that is NOT unmanaged vegetation or water is mostly (mark ONE):"},null,null,null,{"$f":"IF((BuffAllNat=1),\"\", MAX(F189:F190)/MAX(E189:E190))","v":0},"BuffLUpd","Some types of surrounding land cover are more likely to produce propagules of invasive plants that may reduce native plant richness in an adjoining wetland. In calculations, is excluded automatically (cell goes blank) if natural cover in the buffer (see above) is >90%."]
[null,null,{"$f":"F!C256","v":"impervious surface, e.g., paved road, parking lot, building, exposed rock."},{"$f":"F!D256","v":0},0,{"$f":"D189*E189","v":0}]
[null,null,{"$f":"F!C257","v":"bare or nearly bare pervious surface or managed vegetation, e.g., lawn, annual crops, mostly-unvegetated clearcut, landslide, unpaved road, dike."},{"$f":"F!D257","v":0},1,{"$f":"D190*E190","v":0}]
[{"$f":"F!A258","v":"F54"},{"$f":"F!B258","v":"Cliffs, Steep Banks, or Salt Lick "},{"$f":"F!C258","v":"In the AA or within 100 m, there is a known salt lick, or elevated terrestrial features such as cliffs, talus slopes, stream banks, or excavated pits (but not riprap) that extend at least 2 m nearly vertically, are unvegetated, and potentially contain crevices or other substrate suitable for nesting or den areas.  Enter 1 (yes) or 0 (no)."},{"$f":"F!D258","v":0},null,null,{"$f":"D191","v":0},"Rock15","Cliffs and rocky slopes provide nest or dormancy sites for many insect pollinators.  Also, several pollinating butterflies and moths are routinely attracted by salt licks and saline springs."]
[{"$f":"F!A259","v":"F55"},{"$f":"F!B259","v":"New Wetland"},{"$f":"F!C259","v":"The AA is (or is within, or contains) a \"new\" wetland resulting from human actions (e.g., excavation, impoundment) or debris flows,  or other factors affecting what once was upland (non-hydric) soil."},null,null,null,{"$f":"IF((D198=1),\"\",MAX(F193:F197)/MAX(E193:E197))","v":0},"NewWetPD","Unless (or even when) new wetlands are sown with plants, the number of species often remains low for years as colonization gradually occurs and diverse plant communities become established."]
[null,null,{"$f":"F!C260","v":"No"},{"$f":"F!D260","v":0},5,{"$f":"D193*E193","v":0}]
[null,null,{"$f":"F!C261","v":"yes, and created 20 - 100 years ago "},{"$f":"F!D261","v":0},2,{"$f":"D194*E194","v":0}]
[null,null,{"$f":"F!C262","v":"yes, and created 3-20 years ago"},{"$f":"F!D262","v":0},1,{"$f":"D195*E195","v":0}]
[null,null,{"$f":"F!C263","v":"yes, and created within last 3 years"},{"$f":"F!D263","v":0},0,{"$f":"D196*E196","v":0}]
[null,null,{"$f":"F!C264","v":"yes, but time of origin unknown"},{"$f":"F!D264","v":0},1,{"$f":"D197*E197","v":0}]
[null,null,{"$f":"F!C265","v":"unknown if new within 20 years or not"},{"$f":"F!D265","v":0}]
[{"$f":"F!A280","v":"F59"},{"$f":"F!B280","v":"Unvisited Core Area "},{"$f":"F!C280","v":"The percentage of the AA almost never visited by humans during an average growing season probably comprises: [Note: Do not include visitors on trails outside of the AA unless more than half the wetland is visible from the trails and they are within 30 m of the wetland edge.  In that case, imagine the percentage of the AA that would be covered by the trail if it were placed within the AA.]"},null,null,null,{"$f":"MAX(F200:F205)/MAX(E200:E205)","v":0},"Core1pd","Seeds of non-native plants commonly are carried by humans and their pets. Non-native plants can decrease plant species richness of the wetland.  In the Kenai Peninsula of Alaska, significantly fewer nonnative species were found beyond a 500-m distance from a trailhead.  High-use trails, especially those in open-canopied areas, exhibited the greatest numbers of nonnative species at the farthest distances from the trailhead and contained a greater number of less common nonnative species (Bella 2011)."]
[null,null,{"$f":"F!C281","v":"<5% and no inhabited building is within 100 m of the AA"},{"$f":"F!D281","v":0},1,{"$f":"D200*E200","v":0}]
[null,null,{"$f":"F!C282","v":"<5% and inhabited building is within 100 m of the AA"},{"$f":"F!D282","v":0},0,0]
[null,null,{"$f":"F!C283","v":"5-50% and no inhabited building is within 100 m of the AA"},{"$f":"F!D283","v":0},3,0]
[null,null,{"$f":"F!C284","v":"5-50% and inhabited building is within 100 m of the AA"},{"$f":"F!D284","v":0},2,0]
[null,null,{"$f":"F!C285","v":"50-95%"},{"$f":"F!D285","v":0},4,0]
[null,null,{"$f":"F!C286","v":">95% of the AA"},{"$f":"F!D286","v":0},5,0]
[{"$f":"F!A287","v":"F60"},{"$f":"F!B287","v":"Frequently Visited Area"},{"$f":"F!C287","v":"The percentage of the AA visited by humans almost daily for several weeks during an average growing season probably comprises: [Note: Do not include visitors on trails outside of the AA unless more than half the wetland is visible from the trails and they are within 30 m of the wetland edge.   In that case, imagine the percentage of the AA that would be covered by the trail if it were placed within the AA.]"},null,null,null,{"$f":"MAX(F207:F210)/MAX(E207:E210)","v":0},"Core2pd","See above."]
[null,null,{"$f":"F!C288","v":"<5%.  If F59 was answered \">95%\", SKIP to F63 (Consumptive Uses)."},{"$f":"F!D288","v":0},3,{"$f":"D207*E207","v":0}]
[null,null,{"$f":"F!C289","v":"5-50%"},{"$f":"F!D289","v":0},2,{"$f":"D208*E208","v":0}]
[null,null,{"$f":"F!C290","v":"50-95%"},{"$f":"F!D290","v":0},1,{"$f":"D209*E209","v":0}]
[null,null,{"$f":"F!C291","v":">95% of the AA"},{"$f":"F!D291","v":0},0,{"$f":"D210*E210","v":0}]
[{"$f":"F!A292","v":"F61"},{"$f":"F!B292","v":"BMP - Soils"},{"$f":"F!C292","v":"Boardwalks, paved trails, fences or other infrastructure and/or well-enforced regulations appear to effectively prevent visitors from walking on soils within nearly all of the AA when they are unfrozen.  Enter \"1\" if true."},{"$f":"F!D292","v":0},null,null,{"$f":"IF((D205+D207>1),\"\",D211)","v":0},"BMPsoils20","Trampling of native vegetation by recreationists can decrease seed germination and increase vulnerability to invasion by more tolerant invasive plants and ultimately reduce native plant richness.  These and other Best Management Practices (BMPs) potentially reduce such damage.  In calculations, is excluded automatically (cell goes blank) if last choice in F59 was chosen AND first choice in F60 was chosen."]
[{"$f":"F!A328","v":"F69"},{"$f":"F!B328","v":"Plants or Animals of Conservation Concern"},{"$f":"F!C328","v":"If required, survey the AA for plant or animal species believed to be of conservation concern in Alberta (see list on Form F in Appendix A of Manual).  Do so at appropriate times of the year, especially if the data review conducted during the office phase of this assessment indicated their past presence in the general vicinity.  If you do detect these species or have reliable knowledge of their recent (within ~5 years) occurrence within the AA, indicate that below.  "},null,null,null,null,"RarePlant"]
[null,null,{"$f":"F!C329","v":"One or more of the rare plant species was detected within the AA (Appendix A, Table A.4)."},{"$f":"F!D329","v":0},null,null,{"$f":"IF((D213=1),1,\"\")","v":""}]
[{"$f":"S!A3","v":"S5"},{"$f":"S!B3","v":"Altered Timing of Water Inputs"},{"$f":"S!E17","v":"Stressor Subscore="},{"$f":"S!F17","v":0},null,null,{"$f":"IF((AllSat+AllSat1>0),\"\", 1-D214)","v":1},"AltTime20","The germination of many plant species is triggered by the interaction of water conditions and season (light). Homogenization or alteration of the natural water regime can thus encourage invasive species at the expense of native flora. Inundation at aberrant times of the year can reduce native plant diversity because most native species have evolved in close synchronization with natural seasonal water regimes. Monthly timing of first soil moistening may be more important than duration of moist period before inundation and length of inundation., for determining the number of plants and number of species that germinate (Bliss & Zedler 1997). Any development that involves increasing the area of lawn or impervious surface is likely to increase runoff amount and concentrate it within shorter time periods, i.e. “pulses” “flashiness” (Booth & Jackson 1997, Booth et al. 2002, DeGasperi et al. 2009). This has been shown to make wetlands more susceptible to invasion by non-native plants (Magee & Kentula 2005). However, one study found that forested wetlands in developed landscapes had community composition and structure similar to those in undeveloped landscapes, with number of exotic species being no greater (Ehrenfeld 2005).  In calculations, is excluded automatically (cell goes blank) if wetland never has surface water during an average year."]
[{"$f":"S!A18","v":"S6"},{"$f":"S!B18","v":"Accelerated Inputs of Contaminants and/or Salts"},null,{"$f":"S!F32","v":0},null,null,{"$f":"1-D215","v":1},"Toxic20","Fertilizers, herbicides, and other pollutants can alter the composition and sometimes the diversity of the plant community within a wetland.  Pollinators are extremely sensitive to commonly used pesticides."]
[{"$f":"S!A64","v":"S9"},{"$f":"S!B64","v":"Soil or Sediment Alteration Within the Assessment Area"},{"$f":"S!E81","v":"Stressor Subscore="},{"$f":"S!F81","v":0},null,null,{"$f":"1-D216","v":1},"SedDisturb20","Especially in organic and clay soils, trampling and soil compaction results in direct loss of vegetation, changes the soil chemistry and hydrology, reduces seed germination, and facilitates the invasion by exotic species.  Collectively these usually reduce richness of native plants within a wetland."]
[null,null,null,null,null,null,null," "]
[null,null,"Vegetation Form & Distribution [Vstruc]"]
[null,"Wetlands <10 hectares:","AVERAGE(InterspersPD, WoodyCovPD, HerbWood15, ClassRichIn15, wood2pd, herbdom15, HardwdPD, dbhPD, sedgePD, forbsPD)",null,null,null,{"$f":"IF((GT10HA=1),G220,IFERROR(AVERAGE(InterspersPD, WoodyCovPD,HerbWood15, ClassRichIn15, wood2pd, herbdom15, HardwdPD, dbhPD, sedgePD, forbsPD),\"\"))","v":2.5000000000000001E-2}]
[null,"Wetlands >10 hectares:","Substituted MixWaterVeg, MixHerbWood, WetWooded",null,null,null,{"$f":"IFERROR(AVERAGE(MixWaterVeg, MixHerbWood, WetWooded, ClassRichIn15, wood2pd, herbdom15, HardwdPD, dbhPD, sedgePD, forbsPD),\"\")","v":3.5714285714285712E-2}]
[]
[null,null,"Wetland Productivity [CfixV]"]
[null,null,"AVERAGE(GrowDD, RipFloodpl, Spring, InfloPD, SoilTexPD, WettypePD, MossPD, BeaverPD, NfixPD, NewWetPD, FlucPD, Depth15)",null,null,null,{"$f":"IFERROR(AVERAGE(GrowDD, RipFloodpl, Spring, InfloPD, SoilTexPD, WettypePD, MossPD, BeaverPD, NfixPD, NewWetPD, FlucPD, Depth15),\"\")","v":0}]
[]
[null,null,"Habitable Substrate [Vspace]"]
[null,"Wetlands <10 hectares:","[ (AVERAGE(WidthPD, PondedOWpctPD, PersisPD) + AVERAGE(DownedWood15, Snags15, GirregPD, Rock15) ] /2",null,null,null,{"$f":"IF((GT10HA=1),G227, IFERROR(IF((AllSat+AllSat>0),\"\",IF((SmallAA=1),\"\",(AVERAGE(WidthPD,PondedOWpctPD,PersisPD)+AVERAGE(DownWood15,Snags15,GirregPD,Rock15))/2)),\"\"))","v":0}]
[null,"Wetlands >10 hectares:","Substituted 1-OWpct",null,null,null,{"$f":"IFERROR(IF((AllSat+AllSat>0),\"\",IF((SmallAA=1),\"\",(AVERAGE(WidthPD, 1-OWpct, PersisPD) + AVERAGE(DownWood15, Snags15, GirregPD, Rock15)) /2)),\"\")","v":0.25}]
[]
[null,null,"Offsite Habitat Influence [Vscape]"]
[null,null,"AVERAGE(PerimNatCov,NatCov1k, WetDens1k, ClassRich1k, VegCon1k, BuffLUpd, NatVegCApd)",null,null,null,{"$f":"IFERROR(AVERAGE(PerimNatCov,NatCov1k, WetDens1k, ClassRich1k, VegCon1k, BuffLUpd, CUbuffNatPct14),\"\")","v":0}]
[]
[null,null,"Stressors (Lack of) [StressV]"]
[null,null,"[ Invasives + AVERAGE(1-WQrisk, Dist2DevCrop, 1-RdDens1k, Dist2Road, DistPop, Core1pd, Core2pd, BMPsoils20, WeedSourcePD, AltTime20, Toxic20, SedDisturb20) ] / 2",null,null,null,{"$f":"IFERROR((Invasives + AVERAGE(1-WQrisk, Dist2DevCrop, 1-RdDens1k, Dist2Road, DistPop, Core1pd, Core2pd, BMPsoils20, WeedSourcePD, AltTime20, SedDisturb20)) / 2,\"\")","v":0.25}]
[]
[null,null,"ABWRET-A FUNCTION MODEL"]
[null,null,"Native Plant & Pollinator Habitat"]
[null,null,"IF((RarePlant=1),10, 10*AVERAGE(RarePlantRange, UniqClass, AVERAGE(Vstruc, Vspace, CfixV, Vscape, StressV))",null,null,null,{"$f":"IF((RarePlant=1),10, 10*AVERAGE(RarePlantRange, UniqClass, Vstruc1a, Vspace1a, CfixV1a, Vscape1a, StressV1a))","v":0.55000000000000004}]
[null,null,null,null,null,null,null,null,"Literature Cited"]
[null,null,"ABWRET-E model:",null,null,null,null,null,"Allombert, S., S. Stockton, and J.-L. Martin. 2005. A natural experiment on the impact of overabundant deer on forest invertebrates. Conservation Biology 19:1917-1929."]
[null,1,"Calculate these averages:",null,null,null,null,null,"Alsfeld, A. J., J. L. Bowman, and A. Deller-Jacobs. 2009. Effects of woody debris, microtopography, and organic matter amendments on the biotic community of constructed depressional wetlands. Biological Conservation 142:247-255."]
[null,"a","AVERAGE (WetVegArea, ClassRichIn, MixHerbWood)",{"$f":"IFERROR(AVERAGE(WetVegArea, ClassRichIn, MixHerbWood),\"\")","v":""},null,null,null,null,"Anderson, P. D. and M. A. Meleason. 2009. Discerning responses of down wood and understory vegetation abundance to riparian buffer width and thinning treatments: an equivalence-inequivalence approach. Canadian Journal of Forest Research 39:2470-2485."]
[null,"b","AVERAGE(MarshFenSwamp_PctWet, 1-OWpct, MixWaterVeg, RipFloodpl)",{"$f":"IFERROR(AVERAGE(MarshFenSwamp, 1-OWpct, MixWaterVeg, RipFloodpl),\"\")","v":1},null,null,null,null,"Baldwin, L. K. and G. E. Bradfield. 2005. Bryophyte community differences between edge and interior environments in temperate rain-forest fragments of coastal British Columbia. Canadian Journal of Forest Research 35:580-592."]
[null,"c","AVERAGE (ClassRich1k, WetDens1k)",{"$f":"IFERROR(AVERAGE(ClassRich1k, WetDens1k),\"\")","v":""},null,null,null,null,"Baldwin, L. K. and G. E. Bradfield. 2007. Bryophyte responses to fragmentation in temperate coastal rainforests: a functional group approach. Biological Conservation 136:408-422."]
[null,"d","AVERAGE(DistDevCrop, PerimNatCov, NatCov1k, RdDens1k, DistRd)",{"$f":"IFERROR(AVERAGE(Dist2DevCrop, PerimNatCov, NatCov1k, RdDens1k, Dist2Road),\"\")","v":""},null,null,null,null,"Bayley, S. E. and J. K. Guimond. 2008. Effects of river connectivity on marsh vegetation community structure and species richness in montane floodplain wetlands in Jasper National Park, Alberta, Canada. Ecoscience 15:377-388."]
[null,2,"10*AVERAGE(RarePlantRange, UniqClass, a, b, c, d)",{"$f":"10*AVERAGE(RarePlantRange, UniqClass,D241:D244)","v":10},null,null,null,null,"Bayley, S. E. and J. K. Guimond. 2009. Above ground biomass and nutrient limitations in relation to river connectivity in montane floodplain marshes. Wetlands 29:1243-1254."]
[null,null,null,null,null,null,null,null,"Bedford, B. L. and K. S. Godwin. 2003. Fens of the United States: distribution, characteristics, and scientific connection versus legal isolation. Wetlands 23:608-629."]
[null,null,"ABWRET-E with substitutions:",null,null,null,null,null,"Bella, E. M. 2011. Invasion prediction on Alaska trails: Distribution, habitat, and trail use. Invasive Plant Science and Management 4(3): 296-305."]
[null,1,"Calculate these averages:",null,null,null,null,null,"Benscoter, B. W. and D. H. Vitt. 2008. Spatial patterns and temporal trajectories of the bog ground layer along a post-fire chronosequence. Ecosystems 11:1054-1064."]
[null,null,null,null,null,null,null,null,"Bliss, S. A. and P. H. Zedler. 1997. The germination process in vernal pools: sensitivity to environmental conditions and effects on community structure. Oecologia 113:67-73."]
[null,"a","AVERAGE (WetVegArea, ClassRichIn, HerbWood15)",{"$f":"IFERROR(AVERAGE(WetVegArea, ClassRichIn, HerbWood15),\"\")","v":0},null,null,null,null,"Booth, D. B. and C. R. Jackson. 1997. Urbanization of aquatic systems: Degradation thresholds, stormwater detection, and the limits of mitigation. JAWRA Journal of the American Water Resources Association 33:1077-1090."]
[null,"b","AVERAGE(MarshFenSwamp, PondedOWpctPD, InterspersPD, RipFloodpl)",{"$f":"IFERROR(AVERAGE(MarshFenSwamp, PondedOWpctPD, InterspersPD, RipFloodpl),\"\")","v":0},null,null,null,null,"Booth, D. B., D. Hartley, and R. Jackson. 2002. Forest cover, impervious-surface area, and the mitigation of storm water impacts. Journal of American Water Resources Association 38:835-845."]
[null,"c","AVERAGE (ClassRich1k, WetDens1k)",{"$f":"IFERROR(AVERAGE(ClassRich1k, WetDens1k),\"\")","v":""},null,null,null,null,"Boudreault, C., Y. Bergeron, P. Drapeau, and L. M. Loopez. 2008. Edge effects on epiphytic lichens in remnant stands of managed landscapes in the eastern boreal forest of Canada. Forest Ecology and Management 255:1461-1471."]
[null,"d","AVERAGE(DistDevCrop, PerimNatCov, NatCov1k, RdDens1k, DistRd)",{"$f":"IFERROR(AVERAGE(Dist2DevCrop, PerimNatCov, NatCov1k, RdDens1k, Dist2Road),\"\")","v":""},null,null,null,null,"Cadenasso, M. L. and S. T. A. Pickett. 2001. Effect of edge structure on the flux of species into forest interiors. Conservation Biology 15:91-97."]
[null,2,"10*AVERAGE(RarePlantRange, UniqClass, a, b, c, d)",{"$f":"10*AVERAGE(RarePlantRange, UniqClass,D250:D253)","v":0},null,null,null,null,"Chavez, V. and S. E. Macdonald. 2010. The influence of canopy patch mosaics on understory plant community composition in boreal mixedwood forest. Forest Ecology and Management 259:1067-1075."]
[null,null,null,null,null,null,null,null,"Chipman, S. J. and E. A. Johnson. 2002. Understory vascular plant species diversity in the mixedwood boreal forest of western Canada. Ecological Applications 12:588-601."]
[null,null,null,null,null,null,null,null,"Deal, R. L. 1997. Understory plant diversity in riparian alder-conifer stands after logging in southeast Alaska. US Dept. of Agriculture, Forest Service, Pacific Northwest Research Station, Portland, OR."]
[null,null,null,null,null,null,null,null,"DeGasperi, C. L., H. B. Berge, K. R. Whiting, J. J. Burkey, J. L. Cassin, and R. R. Fuerstenberg. 2009. LIinking hydrologic alteration to biological impairment in urbanizing streams of the Puget Lowland, Washington, USA. Journal of the American Water Resources Association 45:512-533."]
[null,null,null,null,null,null,null,null,"Ehrenfeld, J. G., B. Ravit, and K. Elgersma. 2005. Feedback in the plant-soil system. Annual Review of Environment and Resources 30:75-115."]
[null,null,null,null,null,null,null,null,"Geertsema, M. and J. J. Pojar. 2007. Influence of landslides on biophysical diversity — a perspective from British Columbia. Geomorphology 89:55-69."]
[null,null,null,null,null,null,null,null,"Gignac, L. D. and M. R. T. Dale. 2005. Effects of fragment size and habitat heterogeneity on cryptogram diversity in the low-boreal forest of western Canada. The Bryologist 108:50-66."]
[null,null,null,null,null,null,null,null,"Gignac, L. D. and M. R. T. Dale. 2007. Effects of size, shape, and edge on vegetation in remnants of the upland boreal mixed-wood forest in agro-environments of Alberta, Canada. Canadian Journal of Botany 85:273-284."]
[null,null,null,null,null,null,null,null,"Halpern, C. B. and T. A. Spies. 1995. Plant-species diversity in natural and managed forests of the Pacific-Northwest. Ecological Applications 5:913-934."]
[null,null,null,null,null,null,null,null,"Hanley, T. A. and W. W. Brady. 1997. Understory species composition and production in old-growth western hemlock-Sitka spruce forests of southeastern Alaska. Canadian Journal of Botany 75:574-580."]
[null,null,null,null,null,null,null,null,"Heithecker, T. D. and C. B. Halpern. 2007. Edge-related gradients in microclimate in forest aggregates following structural retention harvests in western Washington. Forest Ecology and Management 248:163-173."]
[null,null,null,null,null,null,null,null,"Hood, G. A. and S. E. Bayley. 2008. Beaver (Castor canadensis) mitigate the effects of climate on the area of open water in boreal wetlands in western Canada. Biological Conservation 141:556-567."]
[null,null,null,null,null,null,null,null,"Houlahan, J. E., P. A. Keddy, K. Makkay, and C. S. Findlay. 2006. The effects of adjacent land use on wetland species richness and community composition. Wetlands 26:79-96."]
[null,null,null,null,null,null,null,null,"Hylander, K., B. G. Jonsson, and C. Nilsson. 2002. Evaluating buffer strips along boreal streams using bryophytes as indicators. Ecological Applications 12:797-806."]
[null,null,null,null,null,null,null,null,"Magee, T. K. and M. E. Kentula. 2005. Response of wetland plant species to hydrologic conditions. Wetlands Ecology and Management 13:163-181."]
[null,null,null,null,null,null,null,null,"Mahaney, W. M., D. H. Wardrop, and R. P. Brooks. 2005. Impacts of sedimentation and nitrogen enrichment on wetland plant community structure. Plant Ecology 175:227-243."]
[null,null,null,null,null,null,null,null,"Malmer, N., C. Albinsson, B. M. Svensson, and B. Wallén. 2003. Interferences between Sphagnum and vascular plants: effects on plant community structure and peat formation. Oikos 100:469-482."]
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[null,null,null,null,null,null,null,null,"Nekola, J. C. and P. S. White. 1999. Distance decay of similarity in biogeography and ecology. Journal of Biogeography 26:867–878."]
[null,null,null,null,null,null,null,null,"Nicholson, B. J. 1995. The wetlands of Elk Island National Park: Vegetation classification, water chemistry, and hydrotopographic relationships. Wetlands 15:119-133."]
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[null,null,null,null,null,null,null,null,"Rooney, R. C. and S. E. Bayley. 2011. Relative influence of local- and landscape-level habitat quality on aquatic plant diversity in shallow open-water wetlands in Alberta's boreal zone: direct and indirect effects. Landscape Ecology 26:1023-1034."]
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[null,null,null,null,null,null,null,null,"Wardrop, D. H. and R. P. Brooks. 1998. The occurrence and impact of sedimentation in central Pennsylvania wetlands. Environmental Monitoring and Assessment 51:119-130."]
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{"sheet":"HU","index":22,"n_rows":98,"n_cols":9,"rows_kept":98,"cut":false,"hidden":false,"merged":[[65,0,69,0],[33,8,37,8],[38,1,44,1],[38,8,44,8],[33,1,37,1],[33,0,37,0],[38,0,44,0],[52,8,60,8],[45,8,49,8],[45,1,49,1],[61,1,64,1],[61,0,64,0],[33,7,37,7],[52,1,60,1],[65,7,69,7],[61,7,64,7],[24,0,27,0],[52,0,60,0],[0,0,0,1],[16,8,22,8],[16,1,22,1],[16,0,22,0],[28,0,32,0],[24,8,27,8],[28,8,32,8],[24,1,27,1],[28,7,32,7],[24,7,27,7],[45,0,49,0],[16,7,22,7],[0,4,0,8],[28,1,32,1],[65,1,69,1],[52,7,60,7],[45,7,49,7],[38,7,44,7],[61,8,64,8],[65,8,69,8]]}
["Human Use              and                    Recognition",null,"Prior designation of the wetland, by a natural resource or environmental protection agency, as some type of special protected area.  Also, the potential and actual use of a wetland for low-intensity outdoor recreation, education, or research.","HU"]
["#","Indicators from Estimator","Scoring Notes",null,null,null,"Normalised Score","Indicator Abbreviation or Formula","Rationale"]
[{"$f":"OF!A9","v":"OF8"},{"$f":"OF!C9","v":"Distance to Nearest Road (from Wetland Edge)"},"Inverse ",null,null,null,{"$f":"IF((Dist2Road=\"\"),\"\",1-Dist2Road)","v":""},"Dist2Road","The frequency of most recreational visits declines with increasing distance from roads."]
[{"$f":"OF!A10","v":"OF9"},{"$f":"OF!C10","v":"Distance to Nearest Well-settled Area"},"Inverse ",null,null,null,{"$f":"IF((DistPop=\"\"),\"\",1-DistPop)","v":""},"DistPop","If accessible, wetlands closer to roads are likely to be visited by more people on foot."]
[{"$f":"OF!A17","v":"OF16"},{"$f":"OF!C17","v":"Fringe Wetland"},null,null,null,null,{"$f":"IF((Fringe=\"\"),\"\",IF((Fringe=1),1,\"\"))","v":""},"Fringe","Fringe wetlands adjoin expanses of open water that are visually appealing as well as providing opportunity for fishing and water sports."]
[{"$f":"OF!A20","v":"OF19"},{"$f":"OF!C20","v":"Alberta Culture Listing of Historic Resources"},"If not on the list then cell turns blank (NULL) and is ignored in calculations rather than reducing the score.",null,null,null,{"$f":"IF((HistList=\"\"),\"\",IF((HistList=1),1,\"\"))","v":""},"HistList","These areas provide opportunities for some recreational uses not possible elsewhere."]
[{"$f":"OF!A22","v":"OF21"},{"$f":"OF!C22","v":"Lacustrine Wetland"},"If not a lake then cell turns blank (NULL) and is ignored in calculations rather than reducing the score.",null,null,null,{"$f":"IF((Lake=\"\"),\"\",IF((Lake=1),1,\"\"))","v":""},"Lake","The expanses of open water that characterise lakes are visually appealing as well as providing opportunity for fishing and water sports."]
[{"$f":"OF!A31","v":"OF30"},{"$f":"OF!C31","v":"% of AA that is Open Water (macro scale)"}," ",null,null,null,{"$f":"IF((OWpct=\"\"),\"\",OWpct)","v":""},"OWpct","see above"]
[{"$f":"OF!A41","v":"OF40"},{"$f":"OF!C41","v":"Road Density in 1km Buffer"},null,null,null,null,{"$f":"IF((RdDens1k=\"\"),\"\",RdDens1k)","v":""},"RdDens1k","Roads provide access that enhances most human uses of wetlands."]
[{"$f":"OF!A42","v":"OF41"},{"$f":"OF!C42","v":"Ecological Reserve or Natural Area "},"If not in a Reserve or Natural Area then cell turns blank (NULL) and is ignored in calculations rather than reducing the score.",null,null,null,{"$f":"IF((Reserve=\"\"),\"\",IF((Reserve=1),1,\"\"))","v":""},"Reserve","These areas provide opportunities for some recreational uses not possible elsewhere."]
[{"$f":"OF!A54","v":"OF53"},{"$f":"OF!C54","v":"Access to Trail Network"},"If no trail is mapped within 100m of wetland then cell turns blank (NULL) and is ignored in calculations rather than its absence reducing the score.",null,null,null,{"$f":"IF((Trail=\"\"),\"\",IF((Trail=1),1,\"\"))","v":""},"Trail","Trails provide access that enhances most human uses of wetlands."]
[{"$f":"OF!A61","v":"OF60"},{"$f":"OF!C61","v":"Water Permanence Probability"}," ",null,null,null,{"$f":"IF((WatProb=\"\"),\"\",WatProb)","v":""},"WatProb","Wetlands whose surface water remains for longer during the year are more visually appealing to many people and provide more opportunities for fishing and water sports."]
[{"$f":"OF!A63","v":"OF62"},{"$f":"OF!C63","v":"AA Size"}," ",null,null,null,{"$f":"IF((WetArea=\"\"),\"\",WetArea)","v":""},"WetArea","People are naturally drawn to larger areas of protected lands and larger water bodies. "]
["#","Indicators from Onsite Visit","Categorical Choices","Data","Weight","Data  x  Weight","Normalised Score","Indicator Abbreviation or Formula","Rationale & Scoring Notes"]
[{"$f":"F!A37","v":"F6"},{"$f":"F!B37","v":"Fringe Wetland"},{"$f":"F!C37","v":"If the AA meets the following conditions, it is a fringe wetland: (a) Open water that adjoins the vegetated wetland in a lake, stream, or river during annual low water condition is much wider than the vegetated wetland, and if the AA adjoins a lake (b) the maximum dimension of the lake is greater than 1 km. If true, enter \"1\" and continue."},{"$f":"F!D37","v":0},null,null,{"$f":"IF((Algae21=1),\"\",IF((D15=1),1,\"\"))","v":""},"Fringe21","Fringe wetlands adjoin expanses of open water that are visually appealing as well as providing opportunity for fishing and water sports.  If wetland is not a fringe wetland, then ignored in calculations rather than being counted as a negative. Also ignored if F20 indicates an unsightly growth of algae or duckweed is dominant."]
[{"$f":"F!A38","v":"F7"},{"$f":"F!B38","v":"Lacustrine Wetland"},{"$f":"F!C38","v":"The AA borders a body of ponded open water whose size -- not counting the vegetated AA -- exceeds 8 hectares (about 300 x 300 m) during most of the growing season.  Enter \"1\" if true, \"0\" if false."},{"$f":"F!D38","v":0},null,null,{"$f":"IF((Algae21=1),\"\", IF((D16=1),1,\"\"))","v":""},"Lake21","The expanses of open water that characterise lakes are visually appealing as well as providing opportunity for fishing and water sports. If wetland is not part of a lake, then ignored in calculations rather than being counted as a negative. Also ignored if F20 indicates an unsightly growth of algae or duckweed is dominant."]
[{"$f":"F!A71","v":"F14"},{"$f":"F!B71","v":"% of Ponded Water That Is Open "},{"$f":"F!C71","v":"In ducks-eye aerial view, the percentage of the ponded water that is open (lacking emergent vegetation during most of the growing season, and unhidden by a forest or shrub canopy) is:"},null,null,null,{"$f":"IF((AllSat+AllSat>0),\"\", IF((NoPonded=1),\"\", IF((SmallAA=1),\"\", IF((Algae21=1),\"\", MAX(F18:F23)/MAX(E18:E23)))))","v":0},"PondedOW pct21","Open water areas, especially if ponded, are visually appealing as well as providing opportunity for fishing and water sports. In calculations, is excluded automatically (cell goes blank) if wetland never has surface water during an average year.  Also is excluded automatically if wetland has no ponded water or is <0.01 ha..  Because the simple presence (rather than amount) of open water matters most, the largest jump in the score occurs when at least a little open water is present.  Also ignored if F20 indicates an unsightly growth of algae or duckweed is dominant."]
[null,null,{"$f":"F!C72","v":"<1% or none, or largest pool occupies <0.01 hectares.  Enter \"1\" and SKIP to F20 (Floating Algae & Duckweed)."},{"$f":"F!D72","v":0},0,{"$f":"D18*E18","v":0}]
[null,null,{"$f":"F!C73","v":"1-5% of the ponded water.  Enter \"1\" and SKIP to F20."},{"$f":"F!D73","v":0},2,0]
[null,null,{"$f":"F!C74","v":"5-30% of the ponded water."},{"$f":"F!D74","v":0},3,0]
[null,null,{"$f":"F!C75","v":"30-70% of the ponded water."},{"$f":"F!D75","v":0},4,0]
[null,null,{"$f":"F!C76","v":"70-99% of the ponded water."},{"$f":"F!D76","v":0},4,0]
[null,null,{"$f":"F!C77","v":"100% of the ponded water. "},{"$f":"F!D77","v":0},4,0]
[{"$f":"F!A100","v":"F20"},{"$f":"F!B100","v":"Floating Algae & Duckweed"},{"$f":"F!C100","v":"At some time of the year, mats of algae and/or duckweed cover most of the AA's otherwise-unshaded water surface or blanket the underwater substrate.  If true, enter \"1\" in next column.  If untrue or uncertain, enter \"0\"."},{"$f":"F!D100","v":0},null,null,{"$f":"IF((AllSat+AllSat>0),\"\", IF((NoPonded=1),\"\", IF((SmallAA=1),\"\", IF((D24=1),0,\"\"))))","v":""},"Algae21","Extensive mats of algae or duckweed are unsightly to most people and discourage recreational use, as well as sometimes posing a health risk. In calculations, is excluded automatically (cell goes blank) if wetland never has surface water during an average year.  Also is excluded automatically if wetland has no ponded water or is <0.01 ha.."]
[{"$f":"F!A266","v":"F56"},{"$f":"F!B266","v":"Visibility"},{"$f":"F!C266","v":"From the best vantage point on public roads, public parking lots, public buildings, or well-defined public trails that intersect, adjoin, or are within 100 m of the wetland, some part of the wetland is (select best case):"},null,null,null,{"$f":"MAX(F26:F28)/MAX(E26:E28)","v":0},"Visibility","Public enjoyment of wetlands is assumed to be greater when most of the wetland can be seen without obstruction by dense shrubs or other features."]
[null,null,{"$f":"F!C267","v":"easily visible"},{"$f":"F!D267","v":0},0,{"$f":"D26*E26","v":0}]
[null,null,{"$f":"F!C268","v":"somewhat visible"},{"$f":"F!D268","v":0},1,{"$f":"D27*E27","v":0}]
[null,null,{"$f":"F!C269","v":"barely or not visible"},{"$f":"F!D269","v":0},2,0]
[{"$f":"F!A270","v":"F57"},{"$f":"F!B270","v":"Ownership"},{"$f":"F!C270","v":"Most of the AA is (select one):"},null,null,null,{"$f":"MAX(F30:F33)/MAX(E30:E33)","v":0},"Ownership","Public lands, especially those where recreation or conservation is a primary designated use, are accessible to more people."]
[null,null,{"$f":"F!C271","v":"publicly owned conservation lands that exclude new timber harvest, roads, mineral extraction, and intensive summer recreation (e.g., off-road vehicles).  Includes most Protected Lands."},{"$f":"F!D271","v":0},4,0]
[null,null,{"$f":"F!C272","v":"publicly owned resource use lands (allowed activities such as timber harvest, mining, or intensive recreation), or unknown.  Includes most Crown Reservations/Notations."},{"$f":"F!D272","v":0},3,0]
[null,null,{"$f":"F!C273","v":"Owned by non-profit conservation organization or lease holder who allows public access."},{"$f":"F!D273","v":0},2,0]
[null,null,{"$f":"F!C274","v":"Other private ownership, including First Nations."},{"$f":"F!D274","v":0},1,0]
[{"$f":"F!A275","v":"F58"},{"$f":"F!B275","v":"Non-consumptive Uses - Actual or Potential"},{"$f":"F!C275","v":"Assuming access permission was granted, select ALL statements that are true of the AA as it currently exists:"},null,null,null,{"$f":"SUM(D35:D38)/4","v":0},"RecreaPoten","Lack of physical barriers, provision of trails, and interpretive signs encourage greater public use of areas. However, some apparent barriers (e.g., deep water, dense brush) may be barriers only to summer recreation; frozen wetlands may enjoy considerable wintertime use."]
[null,null,{"$f":"F!C276","v":"For an average person, walking is physically possible in (not just near) >5% of the AA during most of the growing season, e.g., free of deep water and dense shrub thickets."},{"$f":"F!D276","v":0},1,{"$f":"D35*E35","v":0}]
[null,null,{"$f":"F!C277","v":"Maintained roads, parking areas, or foot-trails are within 10 m of the AA, or the AA can be accessed part of the year by boats arriving via contiguous waters."},{"$f":"F!D277","v":0},1,{"$f":"D36*E36","v":0}]
[null,null,{"$f":"F!C278","v":"Within or near the AA, there is an interpretive center, trails with interpretive signs or brochures, and/or regular guided interpretive tours. "},{"$f":"F!D278","v":0},1,{"$f":"D37*E37","v":0}]
[null,null,{"$f":"F!C279","v":"The AA contains or adjoins a public boat dock or ramp, or is within 1 km of a campground, picnic area, or winter sports park."},{"$f":"F!D279","v":0},1,{"$f":"D38*E38","v":0}]
[{"$f":"F!A280","v":"F59"},{"$f":"F!B280","v":"Unvisited Core Area "},{"$f":"F!C280","v":"The percentage of the AA almost never visited by humans during an average growing season probably comprises: [Note: Do not include visitors on trails outside of the AA unless more than half the wetland is visible from the trails and they are within 30 m of the wetland edge.  In that case, imagine the percentage of the AA that would be covered by the trail if it were placed within the AA.]"},null,null,null,{"$f":"MAX(F40:F45)/MAX(E40:E45)","v":0},"Core1PU","The extent of a wetland that is potentially accessible to visitors influences the frequency of visitation.  Presence of an inhabited building nearby suggests the wetland may be visited more often."]
[null,null,{"$f":"F!C281","v":"<5% and no inhabited building is within 100 m of the AA"},{"$f":"F!D281","v":0},4,{"$f":"D40*E40","v":0}]
[null,null,{"$f":"F!C282","v":"<5% and inhabited building is within 100 m of the AA"},{"$f":"F!D282","v":0},5,0]
[null,null,{"$f":"F!C283","v":"5-50% and no inhabited building is within 100 m of the AA"},{"$f":"F!D283","v":0},2,0]
[null,null,{"$f":"F!C284","v":"5-50% and inhabited building is within 100 m of the AA"},{"$f":"F!D284","v":0},3,0]
[null,null,{"$f":"F!C285","v":"50-95%"},{"$f":"F!D285","v":0},1,0]
[null,null,{"$f":"F!C286","v":">95% of the AA"},{"$f":"F!D286","v":0},0,0]
[{"$f":"F!A287","v":"F60"},{"$f":"F!B287","v":"Frequently Visited Area"},{"$f":"F!C287","v":"The percentage of the AA visited by humans almost daily for several weeks during an average growing season probably comprises: [Note: Do not include visitors on trails outside of the AA unless more than half the wetland is visible from the trails and they are within 30 m of the wetland edge.   In that case, imagine the percentage of the AA that would be covered by the trail if it were placed within the AA.]"},null,null,null,{"$f":"MAX(F47:F50)/MAX(E47:E50)","v":0},"Core2PU","See above."]
[null,null,{"$f":"F!C288","v":"<5%.  If F59 was answered \">95%\", SKIP to F63 (Consumptive Uses)."},{"$f":"F!D288","v":0},0,{"$f":"D47*E47","v":0}]
[null,null,{"$f":"F!C289","v":"5-50%"},{"$f":"F!D289","v":0},1,{"$f":"D48*E48","v":0}]
[null,null,{"$f":"F!C290","v":"50-95%"},{"$f":"F!D290","v":0},2,{"$f":"D49*E49","v":0}]
[null,null,{"$f":"F!C291","v":">95% of the AA"},{"$f":"F!D291","v":0},3,{"$f":"D50*E50","v":0}]
[{"$f":"F!A292","v":"F61"},{"$f":"F!B292","v":"BMP - Soils"},{"$f":"F!C292","v":"Boardwalks, paved trails, fences or other infrastructure and/or well-enforced regulations appear to effectively prevent visitors from walking on soils within nearly all of the AA when they are unfrozen.  Enter \"1\" if true."},{"$f":"F!D292","v":0},null,null,{"$f":"IF((D45+D47>1),\"\",D51)","v":0},"BMPsoilsPU","Such features and practices minimize damage to plants and wildlife and thus help sustain the natural features that attract people to wetlands. In calculations, is excluded automatically (cell goes blank) if last choice in F59 was chosen AND first choice in F60 was chosen."]
[{"$f":"F!A293","v":"F62"},{"$f":"F!B293","v":"BMP - Wildlife Protection"},{"$f":"F!C293","v":"Fences, observation blinds, platforms, paved trails, exclusion periods, and/or well-enforced prohibitions on motorized boats, off-leash pets, and off road vehicles appear to effectively exclude or divert visitors and their pets from the AA at critical times in order to minimize disturbance of wildlife (except during hunting seasons).  Enter \"1\" if true. "},{"$f":"F!D293","v":0},null,null,{"$f":"IF((D45+D47>1),\"\",D52)","v":0},"BMPwildPU","See above."]
[{"$f":"F!A294","v":"F63"},{"$f":"F!B294","v":"Consumptive Uses (Provisioning Services)"},{"$f":"F!C294","v":"Recent evidence was found within the AA of the following potentially-sustainable consumptive uses.  Select all that apply."},null,null,null,{"$f":"IF((D61=1),0,1)","v":1},"Provis21","These provide evidence of direct use of a wetland's resources. If any of these uses are present the indicator gets a score of 1."]
[null,null,{"$f":"F!C295","v":"Low-impact commercial timber harvest (e.g., selective thinning)"},{"$f":"F!D295","v":0}]
[null,null,{"$f":"F!C296","v":"Extraction of surface water without noticeably affecting surface water area, depth, or persistence."},{"$f":"F!D296","v":0}]
[null,null,{"$f":"F!C297","v":"Grazing by livestock"},{"$f":"F!D297","v":0}]
[null,null,{"$f":"F!C298","v":"Harvesting of native plants, native hay, or mushrooms (observed or known, not assumed)"},{"$f":"F!D298","v":0}]
[null,null,{"$f":"F!C299","v":"Hunting (observed or known, not assumed)"},{"$f":"F!D299","v":0}]
[null,null,{"$f":"F!C300","v":"Furbearer trapping"},{"$f":"F!D300","v":0}]
[null,null,{"$f":"F!C301","v":"Fishing (observed or known, not assumed)"},{"$f":"F!D301","v":0}]
[null,null,{"$f":"F!C302","v":"No evidence of any of the above"},{"$f":"F!D302","v":0}]
[{"$f":"F!A303","v":"F64"},{"$f":"F!B303","v":"Domestic Wells"},{"$f":"F!C303","v":"The closest wells or water bodies that currently provide drinking water are:"},null,null,null,{"$f":"MAX(F63:F65)/MAX(E63:E65)","v":0},"Wells21","Depending on local geology, some wetlands recharge groundwater or at least reflect local water table levels. In doing so they may indirectly support wells that provide drinking water to nearby residences."]
[null,null,{"$f":"F!C304","v":"Within 100 m of the AA"},{"$f":"F!D304","v":0},2,{"$f":"D63*E63","v":0}]
[null,null,{"$f":"F!C305","v":"100-500 m away"},{"$f":"F!D305","v":0},1,0]
[null,null,{"$f":"F!C306","v":">500 m away, or no information"},{"$f":"F!D306","v":0},0,0]
[{"$f":"F!A318","v":"F67"},{"$f":"F!B318","v":"Prior Investment in the AA"},{"$f":"F!C318","v":"Mark ALL of the following that apply to this AA:"},null,null,null,{"$f":"SUM(D67:D69)/3","v":0},"Invest21","These represent prior investment of public funds which would be nullified if wetland was destroyed. Score is the sum of the first 3 choices divided by 3."]
[null,null,{"$f":"F!C319","v":"Regulatory Investment: The AA is all or part of a mitigation site used explicitly to offset impacts elsewhere"},{"$f":"F!D319","v":0}]
[null,null,{"$f":"F!C320","v":"Non-regulatory Investment: The AA is part of or contiguous to a wetland on which public or private organizational funds were spent to preserve, create, restore, enhance, the wetland (excluding mitigation wetlands)"},{"$f":"F!D320","v":0}]
[null,null,{"$f":"F!C321","v":"Sustained Scientific Use: Plants, animals, or water in the AA have been monitored for >2 years, unrelated to any regulatory requirements, and data are available to the public.  Or the AA is part of an area that has been designated by an agency or institution as a benchmark, reference, or status-trends monitoring area."},{"$f":"F!D321","v":0}]
[null,null,{"$f":"F!C322","v":"None of the above, or no information for any."},{"$f":"F!D322","v":0}]
[]
[null,null,"Potential Access [Access]"]
[null,null,"[ AVERAGE(1-Dist2Road, RdDens1k, 1-DistPop) +   MAX(Reserve, HistList, Trail) ] /2",null,null,null,{"$f":"IFERROR((AVERAGE(1-Dist2Road, RdDens1k, 1-DistPop) + MAX(Reserve, HistList, Trail)) /2,\"\")","v":0.5}]
[]
[null,null,"Resource Use and Best Management Practices [Use]"]
[null,null,"AVERAGE(Provis21, Visibility, Core1PU, Core2PU, RecreaPot, BMPsoilsPU, BMPwildPU, Wells21)",null,null,null,{"$f":"IFERROR(AVERAGE(Provis21, Visibility, Core1PU, Core2PU, RecreaPoten, BMPsoilsPU, BMPwildPU),\"\")","v":0.14285714285714285}]
[]
[null,null,"Wetland Morphology [Wet]"]
[null,"Wetlands <10 hectares:","IF((Algae=1),0, ELSE:  AVERAGE(WetArea, Fringe21, Lake21,PondedOWpct21, WatProb)",null,null,null,{"$f":"IF((GT10HA=1),G80, IFERROR(IF((Algae21=1),0, AVERAGE(WetArea, Fringe21, Lake21, PondedOWpct21, WatProb)),\"\"))","v":0}]
[null,"Wetlands >10 hectares:","Substituted OWpct",null,null,null,{"$f":"IFERROR(IF((Algae21=1),0, AVERAGE(WetArea, Fringe21, Lake21, OWpct, WatProb)),\"\")","v":""}]
[]
[null,null,"ABWRET-A MODEL"]
[null,null,"Human Use"]
[null,null,"10*AVERAGE(Ownership, Invest21, Access, Use, Wet)",null,null,null,{"$f":"10*AVERAGE(Ownership, Invest21, Access1a, Use1a, Wet1a)","v":1.2857142857142856}]
[]
[null,null,"ABWRET-E model:"]
[null,1,"Calculate these:"]
[null,"a","AVERAGE(1-DistRd, RdDens1k, 1-DistPop, Trail)",{"$f":"IFERROR(AVERAGE(1-Dist2Road, RdDens1k, 1-DistPop, Trail),\"\")","v":1}]
[null,"b","AVERAGE(WetArea, WatProb, OWpct, Fringe, Lake)",{"$f":"IFERROR(AVERAGE(WetArea, WatProb, OWpct, Fringe, Lake),\"\")","v":""}]
[null,"c","MAX(Reserve, HistList)",{"$f":"IFERROR(MAX(Reserve, HistList),\"\")","v":0}]
[null,2,"10*AVERAGE(Public, a, b, c)",{"$f":"10*AVERAGE(Public,D88:D90)","v":5}]
[]
[null,null,"ABWRET-E with substitutions:"]
[null,1,"Calculate these:"]
[null,"a","AVERAGE(1-DistRd, RdDens1k, 1-DistPop, Trail)",{"$f":"IFERROR(AVERAGE(1-Dist2Road, RdDens1k, 1-DistPop, Trail),\"\")","v":1}]
[null,"b","AVERAGE(WetArea, WatProb, PondedOWpct21, Fringe, Lake)",{"$f":"IFERROR(AVERAGE(WetArea, WatProb, OWpct, Fringe, Lake),\"\")","v":""}]
[null,"c","MAX(Reserve, HistList)",{"$f":"IFERROR(MAX(Reserve, HistList),\"\")","v":0}]
[null,2,"10*AVERAGE(Ownership, a, b, c)",{"$f":"10*AVERAGE(Ownership,D95:D97)","v":3.333333333333333}]

{"sheet":"Scores","index":23,"n_rows":42,"n_cols":18,"rows_kept":42,"cut":false,"hidden":false,"merged":[[9,5,10,5],[11,5,12,5],[13,5,14,5],[15,5,16,5],[0,1,0,10],[1,1,1,10],[2,1,2,10],[3,1,3,10],[7,0,7,1],[5,0,5,1]]}
[]
[]
[]
[]
[]
["Scores will appear below after all data are entered in worksheets OF, F, and S.  See Manual for definitions and descriptions of how scores were computed."]
[]
["Results for this Wetland Assessment Area (AA):"]
["Specific Functions:","ABWRET-a ","ABWRET-e Original","ABWRET-e with Substitutions ",null,null,null,1,2,3,12,13,14,15,16,17,20,21]
["Surface Water Storage (WS)",{"$f":"IFERROR(IF(WS!$G111>10,10, IF(WS!$G111<0,0, WS!$G111)),\"\")","v":1.3888888888888886},{"$f":"IFERROR(IF(WS!D122>10,10, IF(WS!$D122<0,0, WS!$D122)),\"\")","v":10},{"$f":"IFERROR(IF(WS!$D133>10,10, IF(WS!$D133<0,0, WS!$D133)),\"\")","v":4},null,"Hydrologic Health (HH)","Min",0.38146855600319618,0.3879099060600823,0.39496340488030385,0.38286594423992659,0.3979163414907726,0.38053993886675308,0.40313545880237883,0.37476716462392645,0.37575957878234906,0.39820114272448415,0.40632160511634668]
["Stream Flow Support (SFS)",{"$f":"IFERROR(IF(SFS!$G54>10,10, IF(SFS!$G54<0,0, SFS!$G54)),\"\")","v":10},{"$f":"IFERROR(IF(SFS!$D62>10,10, IF(SFS!$D62<0,0, SFS!$D62)),\"\")","v":10},{"$f":"IFERROR(IF(SFS!$D70>10,10, IF(SFS!$D70<0,0, SFS!$D70)),\"\")","v":8.3333333333333339},null,null,"Max",1,1,1,1,1,1,1,1,1,1,1]
["Streamwater Cooling (WC)",{"$f":"IFERROR(IF(WC!$G82>10,10, IF(WC!$G82<0,0, WC!$G82)),\"\")","v":0.625},{"$f":"IFERROR(IF(WC!$D90>10,10, IF(WC!$D90<0,0, WC!$D90)),\"\")","v":0},{"$f":"IFERROR(IF(WC!$D98>10,10, IF(WC!$D98<0,0, WC!$D98)),\"\")","v":0},null,"Water Quality (WQ)","Min",0.25863933097674363,0.34727702234619384,0.30285867218608453,0.35432615768101111,0.31858341840950755,0.28887362019675245,0.21930329872107185,0.33971224759248353,0.32744410227204629,0.37969647461973483,0.2417358565152678]
["Sediment & Toxicant Retention & Stabilization (SR)",{"$f":"IFERROR(IF(SR!$G105>10,10, IF(SR!$G105<0,0, SR!$G105)),\"\")","v":0.20833333333333331},{"$f":"IFERROR(IF(SR!$D110>10,10, IF(SR!$D110<0,0, SR!$D110)),\"\")","v":10},{"$f":"IFERROR(IF(SR!$D115>10,10, IF(SR!$D115<0,0, SR!$D115)),\"\")","v":3.333333333333333},null,null,"Max",1,1,1,1.0000000000433955,1.0000000000433955,1,1,1,1,1,1]
["Phosphorus Retention (PR)",{"$f":"IFERROR(IF( PR!$G117>10,10, IF( PR!$G117<0,0, PR!$G117)),\"\")","v":0.37037037037037035},{"$f":"IFERROR(IF(PR!$D124>10,10, IF(PR!$D124<0,0, PR!$D124)),\"\")","v":10},{"$f":"IFERROR(IF( PR!$D131>10,10, IF( PR!$D131<0,0, PR!$D131)),\"\")","v":3.333333333333333},null,"Ecological Health (EH)","Min",0.20906835744294067,0.20663912836453724,0.23643943266190853,0.20093675118837312,0.3003400418268749,0.26442553415235687,0.32068011519767398,0.19077169554891751,0.19957947872258952,0.23401677143495078,0.30261006371701371]
["Nitrate Removal & Retention (NR)",{"$f":"IFERROR(IF(NR!$G156>10,10, IF(NR!$G156<0,0, NR!$G156)),\"\")","v":0.91666666666666663},{"$f":"IFERROR(IF(NR!$D166>10,10, IF(NR!$D166<0,0, NR!$D166)),\"\")","v":10},{"$f":"IFERROR(IF(NR!$D176>10,10, IF(NR!$D176<0,0, NR!$D176)),\"\")","v":5},null,null,"Max",1,1,1,1,1,1,1,1,1,1,1]
["Organic Nutrient Export (OE)",{"$f":"IFERROR(IF(OE!$G132>10,10, IF(OE!$G132<0,0, OE!$G132)),\"\")","v":0},{"$f":"IFERROR(IF(OE!$D139>10,10, IF(OE!$D139<0,0, OE!$D139)),\"\")","v":0},{"$f":"IFERROR(IF(OE!$D146>10,10, IF(OE!$D146<0,0, OE!$D146)),\"\")","v":0},null,"Human Use (HU)","Min",0.3504861964321529,0.34059811869686502,0.1676767643615607,0.33325326224540158,0.24306378810509882,0.2504515085813161,0.26293493925242845,0.26264718491421241,0.22570416838274976,0.20461057057295381,0.22708410858645089]
["Fish Habitat (FH)",{"$f":"IFERROR(IF(FH!$G142>10,10, IF(FH!$G142<0,0, FH!$G142)),\"\")","v":0},{"$f":"IFERROR(IF(FH!$D150>10,10, IF(FH!$D150<0,0, FH!$D150)),\"\")","v":7.5},{"$f":"IFERROR(IF(FH!$D158>10,10, IF(FH!$D158<0,0, FH!$D158)),\"\")","v":3.75},null,null,"Max",0.9646450320942801,0.91675384370135005,0.93063188482856807,0.94561260957713777,0.92692506856672452,0.9099428735453069,0.92630605465623828,0.91185015497786182,0.90973070267660638,0.92147170655674737,0.93243860473670703]
["Aquatic Invertebrate Habitat (INV)",{"$f":"IFERROR(IF(INV!$G158>10,10, IF(INV!$G158<0,0, INV!$G158)),\"\")","v":2.2023809523809526},{"$f":"IFERROR(IF(INV!$D166>10,10, IF(INV!$D166<0,0, INV!$D166)),\"\")","v":10},{"$f":"IFERROR(IF(INV!$D174>10,10, IF(INV!$D174<0,0, INV!$D174)),\"\")","v":0},null,"Abundance Modifier",null,0,0,-1,0,1,1,1,0,-1,1,1]
["Amphibian Habitat (AM)",{"$f":"IFERROR(IF(AM!$G150>10,10, IF(AM!$G150<0,0, AM!$G150)),\"\")","v":2.625},{"$f":"IFERROR(IF(AM!$D158>10,10, IF(AM!$D158<0,0, AM!$D158)),\"\")","v":10},{"$f":"IFERROR(IF(AM!$D166>10,10, IF(AM!$D166<0,0, AM!$D166)),\"\")","v":0}]
["Waterbird Habitat (WB)",{"$f":"IFERROR(IF(WB!$G173>10,10, IF(WB!$G173<0,0, WB!$G173)),\"\")","v":0.26666666666666666},{"$f":"IFERROR(IF(WB!$D182>10,10, IF(WB!$D182<0,0, WB!$D182)),\"\")","v":10},{"$f":"IFERROR(IF(WB!$D191>10,10, IF(WB!$D191<0,0, WB!$D191)),\"\")","v":0},null,"Normalization","Percentile","Percentile Value"]
["Songbird, Raptor, & Mammal Habitat (SBM)",{"$f":"IFERROR(IF(SBM!$G184>10,10, IF(SBM!$G184<0,0, SBM!$G184)),\"\")","v":1.375},{"$f":"IFERROR(IF(SBM!$D193>10,10, IF(SBM!$D193<0,0, SBM!$D193)),\"\")","v":10},{"$f":"IFERROR(IF(SBM!$D202>10,10, IF(SBM!$D202<0,0, SBM!$D202)),\"\")","v":5},null,"Normal",90,0.81938841452542677]
["Native Plant & Pollinator Habitat (PH)",{"$f":"IFERROR(IF(PH!$G237>10,10, IF(PH!$G237<0,0, PH!$G237)),\"\")","v":0.55000000000000004},{"$f":"IFERROR(IF(PH!$D245>10,10, IF(PH!$D245<0,0, PH!$D245)),\"\")","v":10},{"$f":"IFERROR(IF(PH!$D254>10,10, IF(PH!$D254<0,0, PH!$D254)),\"\")","v":0},null,null,70,0.74417673953415298]
["Human Use & Recognition (HU)",{"$f":"IFERROR(IF(HU!$G84>10,10, IF(HU!$G84<0,0, HU!$G84)),\"\")","v":1.2857142857142856},{"$f":"IFERROR(IF(HU!$D91>10,10, IF(HU!$D91<0,0, HU!$D91)),\"\")","v":5},{"$f":"IFERROR(IF(HU!$D98>10,10, IF(HU!$D98<0,0, HU!$D98)),\"\")","v":3.333333333333333},null,null,40,0.70702902070167029]
[null,null,null,null,null,"Raw",90,0.86805007680930846]
[null,null,null,null," the top 5% and bottom 5% would not be modified.",null,70,0.80133727567733504]
[null,null,null,null,null,null,40,0.76935623018830834]
[]
[null,null,null,null,null,"Function_175Sites","Max_A","Min_A","Max_E","Min_E","Max_Esub","Min_Esub"]
[null,null,null,null,null,"WS",10,2.9609907107916666,10,3.0073654445999995,10,3.5869274201111105]
[null,null,null,null,null,"SFS",6.1712860975396824,0,6.9788626601785717,1.2797534755357143,7.4621049941071433,1.1586413719642858]
[null,null,null,null,null,"WC",10,1.4820157983333333,8.7289316024999994,0,8.375,0]
[null,null,null,null,null,"SR",10,3.0079284411111109,10,0.91138392999999995,10,0.61567322750000009]
[null,null,null,null,null,"PR",10,2.8904090020202018,10,1.7198025275000002,10,1.5583395691666666]
[null,null,null,null,null,"NR",10,3.8062425370857147,5.6068148595833334,1.4349005495833334,6.3240268487500009,1.4229982286904761]
[null,null,null,null,null,"OE",10,2.360228437694444,8.718224491111112,0,8.2099468688888884,0]
[null,null,null,null,null,"FH",7.3082156069428574,0,8.485291530833333,0.20746534866666663,6.4046848511111101,0.22445486333333334]
[null,null,null,null,null,"INV",8.9155505651102285,1.4648811356635802,9.3349742688888888,2.1916276791666665,8.1419086494444457,1.981579985277778]
[null,null,null,null,null,"AM",7.5683567906899354,0.83502837383487638,9.6601986816666656,0.96823104583333319,8.5160458280555549,0.96187725499999999]
[null,null,null,null,null,"WB",10,2.170015327568783,10,1.3613012483333333,10,1.3535442445833334]
[null,null,null,null,null,"SBM",7.8589086118301585,2.3605539013455021,7.871541955833333,3.487968728611111,8.0435897574074087,3.54272569375]
[null,null,null,null,null,"PH",7.6962532355238098,2.1835193160544217,7.9573209432500001,2.886473983138889,8.5472264932962965,2.8834063551666667]
[null,null,null,null,null,"HU",6.4603991528285718,1.2687647593333335,8.5681033908749988,0.74711518975000002,8.1682851186250005,1.3721151897500001]

{"sheet":"Table 1","index":24,"n_rows":15,"n_cols":2,"rows_kept":15,"cut":false,"hidden":false,"merged":[]}
["SOIL TEXTURE CLASS (as mapped by AGRASID)","Score for Relative Capacity for Infiltration (Assumed)"]
["Very Coarse",1]
["Moderately Coarse & Very Coarse",0.9]
["Medium & Very Coarse",0.7]
["Peat & Very Coarse",0.8]
["Moderate & Coarse",0.5]
["Moderately Coarse & Medium",0.5]
["Moderately Coarse & Peat",0.6]
["Medium",0.4]
["Medium & Peat",0.5]
["Fine & Medium",0.30000000000000004]
["Medium & Fine",0.3]
["Peat",0.19999999999999996]
["Fine",9.9999999999999978E-2]
["Undifferentiated","blank (=NULL)"]

{"sheet":"Table 2","index":25,"n_rows":15,"n_cols":2,"rows_kept":15,"cut":false,"hidden":false,"merged":[]}
["SOIL TEXTURE CLASS (as mapped by AGRASID)","Score for Relative Capacity for Phosphorus Adsorption (Assumed)"]
["Fine",1]
["Fine & Medium",0.9]
["Medium & Fine",0.9]
["Peat",0.7]
["Medium & Peat",0.6]
["Peat & Very Coarse",0.5]
["Moderately Coarse & Peat",0.5]
["Medium",0.5]
["Moderate & Coarse",0.4]
["Moderately Coarse & Medium",0.4]
["Medium & Very Coarse",0.3]
["Moderately Coarse & Very Coarse",0.2]
["Very Coarse",0.1]
["Undifferentiated","blank (=NULL)"]

{"sheet":"Table 3","index":26,"n_rows":15,"n_cols":2,"rows_kept":15,"cut":false,"hidden":false,"merged":[]}
["SOIL TEXTURE CLASS (as mapped by AGRASID)","Score for ORGANIC CONTENT (Assumed)"]
["Peat",1]
["Medium & Peat",0.9]
["Moderately Coarse & Peat",0.8]
["Peat & Very Coarse",0.7]
["Fine",0.6]
["Fine & Medium",0.5]
["Medium & Fine",0.5]
["Medium",0.4]
["Moderately Coarse & Medium",0.3]
["Moderate & Coarse",0.2]
["Very Coarse",0.1]
["Moderately Coarse & Very Coarse",0.1]
["Medium & Very Coarse",0.1]
["Undifferentiated","blank (=NULL)"]