Abstract

Wetland indices of biological integrity (IBIs) are a common component in monitoring the wetland water resources as required by the United States’ Clean Water Act (CWA). The effectiveness of an IBI to monitor disturbance is dependent on the metrics being consistently responsive to measures of human disturbance within a described classification category. We present IBIs designed for two types of commonly used wetland classification systems – the hydrogeomorphic (HGM) and the National Wetlands Inventory (NWI). The metrics making up the IBIs were derived from anuran, avian, macroinvertebrate, and vegetation communities; each representing increasing levels of resources associated with gathering the necessary data. Knowing which communities’ data best corresponds to impairment can maximize limited wetland monitoring resources, especially if the response differs based on the wetland vegetation type NWI or HGM position on the landscape. By combining these two classification schemes together, to better define a wetland’s form and context on the landscape, more of the variability in community metrics are explained by human impairment. Moreover, when multiple taxa are used within a single wetland classification scheme, the response of the multi-taxa community IBI to the human disturbance gradient is often more sensitive than one-taxa group alone. This approach, a combination of taxa, in hybrid 2-system classification schemes, creates additional utility in measuring the effectiveness of wetland assessments and, or restoration success.

Highlights

  • Under the United States’ Clean Water Act (CWA), individual states have the right to determine water quality standards with respect to differing types of waterbodies

  • This lack of using species assemblages in monitoring comes despite the U.S Environmental Protection Agency (EPA) previously announcing stan­ dardized guidelines based on three tiers to link a wetland’s condition to its ability to perform wetland functions with the hopes to lead to an improved regulatory framework (U.S Environmental Protection Agency, 2003)

  • We developed a series of wetland indices of biological integrity using anuran, avian, macro­ invertebrate, and vegetative communities (Veselka et al, 2010a; b, Veselka and Anderson, 2013) in 151 wetlands located throughout West Virginia during 2005–2006

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Summary

Introduction

Under the United States’ Clean Water Act (CWA), individual states have the right to determine water quality standards with respect to differing types of waterbodies (e.g., streams, lakes, wetlands). The vegetation criteria tend to be tied to subjective numbers like stems per acre rather than ecological thresholds that must be calibrated for each region (DeBerry et al, 2015) This lack of using species assemblages in monitoring comes despite the U.S Environmental Protection Agency (EPA) previously announcing stan­ dardized guidelines based on three tiers to link a wetland’s condition to its ability to perform wetland functions with the hopes to lead to an improved regulatory framework (U.S Environmental Protection Agency, 2003). This framework is based on spatial scales.

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