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ASTM E 2205/E2205M : 2022

Current

Current

The latest, up-to-date edition.

Standard Guide for Risk-Based Corrective Action for Protection of Ecological Resources

Available format(s)

Hardcopy , PDF

Language(s)

English

Published date

27-02-2023

€94.22
Excluding VAT

Committee
E 50
DocumentType
Guide
Pages
64
PublisherName
American Society for Testing and Materials
Status
Current
Supersedes

1.1This is a guide to risk-based corrective action for the protection of ecological resources and supplements the RBCA process (Guide E2081). The primary objective of the Eco-RBCA process is to provide a flexible framework for a tiered approach to ERA and risk management decision making at chemical release sites. To this end, available guidance documents from various federal and state agencies were reviewed and their common attributes incorporated into this guide, where possible. The Eco-RBCA process complements existing technical and regulatory ecological risk guidance (see 4.2). In particular, it is intended to be compatible with the USEPA programmatic guidelines for ERA (1)2, guidance for the Superfund program (2), and other USEPA (3) risk assessment and corrective-action programs. Eco-RBCA might also be used in conjunction with corrective action strategies that include human health issues (for example, Guide E2081).

1.2Chemical release sites vary greatly in terms of complexity, physical and chemical characteristics, and the risk that they might pose to ecological resources. The Eco-RBCA process, as described in Guide E2081, recognizes this variability and incorporates a tiered approach that integrates site assessment, response actions, and remedial actions with ERA. The process begins with relatively simple analyses in Tier 1 and, if necessary, proceeds to more detailed evaluations in Tier 2 or Tier 3. The process of gathering and evaluating data is conducted in such a manner that only those data that are necessary for a given tier's decision making are collected at each tier. Hence, this can facilitate effective use of resources and reduce initial data requirements.

1.3Eco-RBCA is intended to provide a framework for sites not covered under regulatory programs and for sites under regulatory programs that lack specific guidance. Eco-RBCA may also provide a useful framework to help merge several possible approaches into a single approach when multiple regulatory programs apply. The user should be aware of the federal, state, and local corrective action programs and policies that are applicable for the site and, regardless of the program, that agency approvals might be required to implement the process for completing ERAs.

1.4Various TPDs will need to be made regarding the aspects of Eco-RBCA. These TPDs may cover both the philosophical and methodological aspects, from what values to protect to exactly how the Eco-RBCA process will be performed. TPDs may affect every stage of the process, from the initial site assessment to development and monitoring of the remedy. It is the responsibility of the user to identify the appropriate TPDs. Section 7, Appendix X2, and Guide E2081 provide more detail regarding TPDs in the Eco-RBCA process.

1.5The general performance standard for this document requires that:

1.5.1Applicable TPDs be identified, beginning at the initiation of the Eco-RBCA process, and as appropriate, at later stages;

1.5.2Data used in the Eco-RBCA process be of sufficient quantity and quality to answer the questions and support the decisions made at the tier of investigation;

1.5.3Site assessments be distinguished into tiers of appropriate levels of evaluation;

1.5.4Actions taken should integrate the Eco-RBCA process for the protection of relevant ecological receptors and habitats and RBCA for the protection of human health (see Guide E2081), as appropriate;

1.5.5Applicable federal, state, and local laws and regulations be followed; and

1.5.6Potential adverse effects on relevant ecological receptors and habitats be considered when selecting remedial action alternatives. The remedial action alternatives should be consistent with the TPDs and the RBCA process (see Guide E2081).

1.6Ecological resources are the focus of this guide; risks to human health are addressed for petroleum releases and chemical releases in other ASTM RBCA standards (Guides E1739 and E2081). There are many features common to all three of the RBCA guides. These three guides share the basic elements of RBCA: (1) site assessment; (2) tiered evaluations of exposure, effects, and risk; (3) risk-based decision making; and (4) response, remedial action, and monitoring. There are a number of distinctions between human health and ecological risk assessments. For example, while human health risk assessments focus on individuals, evaluations of ecological risk typically focus on populations, communities, or ecosystems. Exceptions are species or critical habitats designated for special protection (for example, endangered or culturally-important species). Biological data to support an ERA are more amenable to direct field observation than are human exposure and epidemiological data.

1.7The Eco-RBCA process addresses current and potential future risks to relevant ecological receptors and habitats at chemical release sites. It is not intended to apply to current permitted releases and permit applications.

1.8Eco-RBCA focuses on chemical stressors. However, the user may need to consider biological or physical stressors at the site or effects from chemical sources unrelated to the site.

1.9The process described in this guide integrates the principles of current ERA practices with site assessment activities and remedial-action selection to ensure that the risk management decision protects ecological resources. Fig. 1 illustrates the following activities in Eco-RBCA and those described in Section 7 (7.1 – 7.10):

1.9.1Step 1—Initial Site Assessment;

1.9.2Step 2—Decision Point;

1.9.3Step 3—Tier 1 Ecological Risk Assessment;

1.9.4Step 4—Tier 1 Decision Point;

1.9.5Step 5—Tier 2 Ecological Risk Assessment;

1.9.6Step 6—Tier 2 Decision Point;

1.9.7Step 7—Tier 3 Ecological Risk Assessment;

1.9.8Step 8—Tier 3 Decision Point;

1.9.9Step 9—Implementing the Remedial Action Program; and

1.9.10Step 10—Monitoring Programs (7.10).

1.9.11The above steps can be applied in a flexible manner. It may not be necessary to conduct a full tier of evaluation if existing site information indicates that a subsequent tier is more applicable to address site-specific concerns. Where experience indicates that a more sophisticated assessment is warranted at a site, the user may elect to proceed conceptually through any earlier tiers to conduct a site-specific assessment typical of Tier 2 or Tier 3. Additionally, the decision points in Steps 4, 6, and 8 allow the user to exit the tiered evaluation process and select the appropriate remedial action once adequate information is available for decision making.

1.10This guide is organized as follows:

1.10.1Section 2 lists referenced ASTM documents;

1.10.2Section 3 defines terminology used in this guide;

1.10.3Section 4 describes the significance and use of this guide;

1.10.4Section 5 describes the tiered approach to the Eco-RBCA process;

1.10.5Sections 6 and 7 presents Eco-RBCA procedures in a step-by-step process; and

1.10.6The reference section provides all documents cited in this guide.

1.11This guide also includes the following appendices, which are provided as supplemental information and are not included as mandatory sections of this guide:

1.11.1Appendix X1 presents information related to risk management issues;

1.11.2Appendix X2 presents issues regarding TPDs;

1.11.3Appendix X3 presents information on the activities occurring in each tier of the Eco-RBCA process;

1.11.4Appendix X4 describes screening criteria and how they can be applied within the Eco-RBCA framework;

1.11.5Appendix X5 presents the selection and use of relevant ecological screening benchmarks;

1.11.6Appendix X6 includes two examples of the application of the Eco-RBCA framework; and

1.11.7Appendix X7 presents information on uncertainty and its role in Eco-RBCA.

1.12The values stated in either SI units or inch-pound units are to be regarded separately as standard. The values stated in each system may not be exact equivalents; therefore, each system shall be used independently of the other. Combining values from the two systems may result in non-conformance with the standard.

1.13This international standard was developed in accordance with internationally recognized principles on standardization established in the Decision on Principles for the Development of International Standards, Guides and Recommendations issued by the World Trade Organization Technical Barriers to Trade (TBT) Committee.

ASTM E 2081 : 2022 Standard Guide for Risk-Based Corrective Action
ASTM E 2385 : 2011 : R2016 Standard Guide for Estimating Wildlife Exposure Using Measures of Habitat Quality
ASTM E 3163 : 2018 Standard Guide for Selection and Application of Analytical Methods and Procedures Used during Sediment Corrective Action

ASTM E 1739 : 1995 : R2015 Standard Guide for Risk-Based Corrective Action Applied at Petroleum Release Sites (Withdrawn 2024)
ASTM E 3242 : 2023 Standard Guide for Developing Representative Background Concentrations at Sediment Sites—Data Evaluation and Development Methodologies
ASTM E 3163 : 2024 Standard Guide for Contaminated Sediment Site Risk-Based Corrective Action—Selection and Application of Analytical Methods and Test Procedures
ASTM E 3242 : 2020 Standard Guide for Determination of Representative Sediment Background Concentrations
ASTM E 3164 : 2023 Standard Guide for Contaminated Sediment Site Risk-Based Corrective Action – Baseline, Remedy Implementation and Post-Remedy Monitoring Programs
ASTM E 3164 : 2018 Standard Guide for Sediment Corrective Action – Monitoring

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