Barron Mace G, Wharton Steven R
Gulf Ecology Division, U.S. Environmental Protection Agency, 1 Sabine Island Drive, Gulf Breeze, Florida 32561, USA.
Integr Environ Assess Manag. 2005 Nov;1(4):320-32.
This review evaluates the methodologies of 13 screening value (SV) compilations that have been commonly used in ecological risk assessment (ERA), including compilations from state and U.S. federal agencies, the Oak Ridge National Laboratory (ORNL), Canada, The Netherlands, and Australia. The majority of surfacewater SVs were primarily derived for the protection of aquatic organisms using 2 approaches: (1) a statistical assessment of toxicity values by species groupings, such as "ambient water quality criteria," or (2) extrapolation of a lowest observed adverse effect level determined from limited toxicity data using an uncertainty factor. Sediment SVs were primarily derived for the protection of benthic invertebrates using 2 approaches: (1) statistical interpretations of databases on the incidence of biological effects and chemical concentrations in sediment, or (2) values derived from equilibrium partitioning based on a surfacewater SV. Soil SVs were derived using a diversity of approaches and were usually based on the lowest value determined from soil toxicity to terrestrial plants or invertebrates and, less frequently, from modeled, incidental soil ingestion or chemical accumulation in terrestrial organisms. The various SV compilations and methodologies had varying levels of conservatism and were not consistent in the pathways and receptors considered in the SV derivation. Many SVs were derived from other compilations and were based on outdated values, or they relied on only older toxicity data. Risk assessors involved in ERA should carefully evaluate the technical basis of SVs and consider the uncertainty in any value used to determine the presence or absence of risk and the need for further assessment.
本综述评估了生态风险评估(ERA)中常用的13种筛选值(SV)汇编方法,包括来自美国各州和联邦机构、橡树岭国家实验室(ORNL)、加拿大、荷兰和澳大利亚的汇编。大多数地表水SV主要通过两种方法得出,用于保护水生生物:(1)按物种分组对毒性值进行统计评估,如“环境水质标准”;或(2)使用不确定性系数,根据有限毒性数据确定的最低观察到的有害效应水平进行外推。沉积物SV主要通过两种方法得出,用于保护底栖无脊椎动物:(1)对沉积物中生物效应发生率和化学浓度数据库的统计解释;或(2)基于地表水SV通过平衡分配得出的值。土壤SV通过多种方法得出,通常基于从土壤对陆生植物或无脊椎动物的毒性确定的最低值,较少情况下基于陆生生物中模拟的偶然土壤摄入或化学积累。各种SV汇编和方法的保守程度各不相同,在SV推导中考虑的途径和受体也不一致。许多SV源自其他汇编,基于过时的值,或者仅依赖较旧的毒性数据。参与ERA的风险评估人员应仔细评估SV的技术基础,并考虑用于确定风险存在与否的任何值中的不确定性以及进一步评估的必要性。