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Standard Guide for Selecting and Using Ecological Endpoints for Contaminated Sites 选择和使用污染场地生态端点的标准指南
发布日期: 2020-11-01
1.1 本指南涵盖了生态端点(评估和测量端点)的识别、选择和使用方法 ( 1- 8. ) 2. 在当前和未来的土地利用下,易受与特定地点废物和受污染介质相关的化学和非化学应激源或药剂的直接和间接影响。它不涉及非现场特定研究(例如,化学特定或区域风险评估)或非生物介质(土壤、水或空气)测量的评估和测量终点。 1.2 本指南仅涉及评估和测量终点的识别、选择和使用,而不是污染场地生态评估或生态风险评估中发生的全部活动 ( 1. , 3- 8. ) . 这些活动在本指南末尾提供的其他ASTM指南和参考文献中进行了阐述。 1.3 本指南旨在确定以线性或迭代方式进行的筛选、初步、重点、详细和定量生态风险评估所用的评估和测量终点 ( 3. , 8. ) . 这是部分、不完整的可能评估级别列表。在分层生态风险评估中,当计划收集更多数据或获得和评估其他现场数据时,可能需要重新定义生态端点。 1.4 本指南旨在供熟悉风险评估以及生态和生态毒理学概念的训练有素的生物学家、生态学家和生态毒理学专家使用。 1.5 本指南(包括 附录X1 )由一系列选项或说明组成,不建议具体的行动方案,也不提供所有现场应遵循的详细指南。见第2.2.2节 ASTM技术委员会管理条例 . 3. 1.6 本标准并非旨在解决与其使用相关的所有安全问题(如有)。本标准的用户有责任在使用前制定适当的安全、健康和环境实践,并确定监管限制的适用性。 1.7 本国际标准是根据世界贸易组织技术性贸易壁垒(TBT)委员会发布的《关于制定国际标准、指南和建议的原则的决定》中确立的国际公认标准化原则制定的。 ====意义和用途====== 4.1 本指南假设已作出决定,需要对受污染场地进行生态风险评估。在某些情况下,可以在收集任何现场数据之前做出此决定。看见 图1 . 图1 评估终点、测量终点和证据线之间的概念关系(来源:联邦污染场地行动计划(FCSAP)生态风险评估指南,加拿大政府,2012年3月) 4.2 选择评估终点(定义为要保护的生态价值)和测量终点(与评估终点相关的生态特征)是进行生态风险评估的关键步骤。 终点选择确定了那些具有生态意义的影响,而不仅仅是那些不利的影响,从而为做出风险和补救决策提供了更合理、更可靠的基础。 4.3 本指南提供了一种方法,用于在受污染场地的生态风险评估中识别、选择和使用评估和测量端点。之所以制定本指南,是因为没有一种通用、简单的生态健康测量方法可以与人类健康风险评估中使用的测量方法相媲美。必须从压力源的各种个人情况中确定和选择评估和测量终点- ,生态系统和规模特定基础。重要的是要认识到,特定地点可能需要一组不同的生态端点。用于生态风险评估的EPA/100/F15/005通用生态评估端点:第二版,增加了通用生态系统服务端点。2016年7月) 4.4 本指南主要供生物学家、生态学家、生态毒理学家或环境科学家团队在污染现场开始数据收集活动之前制定问题和工作计划时使用 ( 3- 8. , 10 ) . 4.5 生态风险评估通常是一个迭代过程。在许多情况下,它作为一系列层次进行,即桌面/筛选、初步和详细/重点阶段。 本指南可用于完善或修改过程早期阶段开发的评估和测量端点。 4.6 只要在初始或初步问题制定/规划阶段后必须确定和选择评估和测量端点,就可以使用本指南: 4.6.1 分析阶段(暴露评估、危害/影响评估、压力/剂量反应评估; 4.6.2 风险表征阶段;或 4.6.3 修复阶段和可能的后续生态监测。 4.7 本指南旨在用于评估基线条件(当前和未来)以及评估补救措施或纠正措施产生的条件。
1.1 This guide covers an approach to identification, selection, and use of ecological endpoints (both assessment and measurement endpoints) ( 1- 8 ) 2 that are susceptible to the direct and indirect effects of both chemical and non-chemical stressors or agents associated with wastes and contaminated media at specific sites under current and future land uses. It does not address assessment and measurement endpoints for non-site specific studies (for example, chemical-specific or regional risk assessments) or measurements in abiotic media (soil, water, or air). 1.2 This guide addresses only the identification, selection, and use of assessment and measurement endpoints, not the full range of activities that occur in an ecological assessment or ecological risk assessment at a contaminated site ( 1 , 3- 8 ) . These activities are addressed in other ASTM guides and references provided at the end of this guide. 1.3 This guide is intended to identify assessment and measurement endpoints to be used for screening, preliminary, focused, detailed, and quantitative ecological risk assessments conducted in a linear or iterative fashion ( 3 , 8 ) . This is a partial, incomplete listing of possible levels of assessment. In a tiered ecological risk assessment, it may be necessary to redefine ecological endpoints when planning to collect more data or when additional site data are obtained and evaluated. 1.4 This guide is intended to be used by trained biologists, ecologists, and ecotoxicologists familiar with risk assessment, and ecological and ecotoxicological concepts. 1.5 This guide (including Appendix X1 ) consists of a series of options or instructions and does not recommend a specific course of action or provide detailed guidelines to be followed at all sites. See 2.2.2 of Regulations Governing ASTM Technical Committees . 3 1.6 This standard does not purport to address all of the safety concerns, if any, associated with its use. It is the responsibility of the user of this standard to establish appropriate safety, health, and environmental practices and determine the applicability of regulatory limitations prior to use. 1.7 This 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. ====== Significance And Use ====== 4.1 This guide assumes that a decision has been made that an ecological risk assessment is required for a contaminated site. In some cases, this decision could be made before any site data are collected. See Fig. 1 . FIG. 1 Conceptual Relationships between Assessment Endpoints, Measurement Endpoints and Lines of Evidence (Source: Federal Contaminated Sites Action Plan (FCSAP) Ecological Risk Assessment Guidance, Government of Canada, March 2012) 4.2 The selection of assessment endpoints (defined as ecological values to be protected) and measurement endpoints (ecological characteristics related to the assessment endpoints) is a critical step in conducting an ecological risk assessment. Endpoint selection identifies those effects which are ecologically significant and not merely those that are adverse, thus providing a more rational and defensible basis for making risk and remedial decisions. 4.3 This guide provides an approach for identifying, selecting and using assessment and measurement endpoints in an ecological risk assessment for a contaminated site. This guide has been developed because there is no universal, simple measure of ecological health analogous to measures used in human health risk assessment. Assessment and measurement endpoints have to be identified and selected from a variety of individual circumstances on a stressor-, ecosystem- and scale-specific basis. It is important to recognize that a diverse set of ecological endpoints could be required for a specific site. EPA/100/F15/005 Generic Ecological Assessment Endpoints (GEAEs) For Ecological Risk Assessment: Second Edition With Generic Ecosystem Services Endpoints Added. July 2016) 4.4 This guide is intended to be used primarily by a biologist, ecologist, ecotoxicologist, or a team of environmental scientists during problem formulation and work plan development prior to initiating data collection activities at a contaminated site ( 3- 8 , 10 ) . 4.5 Ecological risk assessment is usually an iterative process. In many circumstances it proceeds as a series of tiers, that is, desktop/screening, preliminary, and detailed/focused phases. This guide can be used to refine or modify assessment and measurement endpoints developed in earlier phases of the process. 4.6 This guide can be used whenever assessment and measurement endpoints must be identified and selected following an initial or preliminary problem formulation/planning phase: 4.6.1 Analysis phase (exposure assessment, hazard/effects assessment, stress/dose-response assessment; 4.6.2 Risk characterization phase; or 4.6.3 Remediation phase and possible subsequent ecological monitoring. 4.7 This guide is intended to be used in the evaluation of baseline conditions (current and future) and in the evaluation of conditions resulting from remedial actions or corrective measures.
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