Standard Guide for Estimating Wildlife Exposure Using Measures of Habitat Quality
|Publication Date:||1 December 2004|
|ICS Code (Veterinary medicine):||11.220|
Ecological Risk Assessments (EcoRAs) typically focus on valued wildlife populations. Regulatory authority for conducting EcoRAs derives from various federal laws [for example, Comprehensive Environmental Response, Compensation and Liability Act 1981, (CERCLA), Resource Conservation Recovery Act (RCRA), and Federal Insecticide, Fungicide, and Rodenticide Act, (FIFRA)]. Certain procedures for conducting EcoRAs (1-4)(Footnote 2) have been standardized [E 1689-95(2003) Standard Guide for Developing Conceptual Site Models for Contaminated Sites; E 1848-96(2003) Standard Guide for Selecting and Using Ecological Endpoints for Contaminated Sites; E 2020-99a Standard Guide for Data and Information Options for Conducting an Ecological Risk Assessment at Contaminated Sites; E 2205-02 Standard Guide for Risk-Based Corrective Action for Protection of Ecological resources; E 1739-95(2002) Standard Guide for Risk-Based Corrective Action Applied at Petroleum Release Sites]. Specialized cases for reporting data have also been standardized [E 1849-96(2002) Standard Guide for Fish and Wildlife Incident Monitoring and Reporting] as have sampling procedures to characterize vegetation [E 1923-97(2003) Standard Guide for Sampling Terrestrial and Wetlands Vegetation].
Most states have enacted laws modeled after the federal acts and
follow similar procedures.
Typically, estimates of likely exposure levels to constituents of
potential concern (CoPC) are
compared to toxicity benchmark values or concentration-respon
This guide is intended only as a framework for using measures of habitat quality in species specific habitat suitability models to assist with the calculation of exposure levels in EcoRA. Information from published Habitat Suitability Index (HSI) models (5) is used in this guide. The user should become familiar with the strengths and limitations of any particular HSI model used in order to characterize uncertainty in the exposure assessment (5-7). For species that do not have published habitat suitability models, the user may elect to develop broad categorical descriptions of habitat quality for use in estimating exposure.
Footnote 2 - The boldface numbers in parentheses refer to the list references at the end of this standard.