Romijn C A, Luttik R, van de Meent D, Slooff W, Canton J H
National Institute of Public Health and Environmental Protection (RIVM), Bilthoven, The Netherlands.
Ecotoxicol Environ Saf. 1993 Aug;26(1):61-85. doi: 10.1006/eesa.1993.1041.
Effect assessment on secondary poisoning can be an asset to effect assessments on direct poisoning in setting quality criteria for the environment. This study presents an algorithm for effect assessment on secondary poisoning. The water-fish-fish-eating bird or mammal pathway was analyzed as an example of a secondary poisoning pathway. Parameters used in this algorithm are the bioconcentration factor for fish (BCF) and the no-observed-effect concentration for the group of fish-eating birds and mammals (NOECfish-eater). For the derivation of reliable BCFs preference is given to the use of experimentally derived BCFs over QSAR estimates. NOECs for fish eaters are derived by extrapolating toxicity data on single species. Because data on fish-eating species are seldom available, toxicity data on all birds and mammalian species were used. The proposed algorithm (MAR = NOECfish-eater/BCF) was used to calculate MARS (maximum acceptable risk levels) for the compounds lindane, dieldrin, cadmium, mercury, PCB153, and PCB118. By subsequently, comparing these MARs to MARs derived by effect assessment for aquatic organisms, it was concluded that for methyl mercury and PCB153 secondary poisoning of fish-eating birds and mammals could be a critical pathway. For these compounds, effects on populations of fish-eating birds and mammals can occur at levels in surface water below the MAR calculated for aquatic ecosystems. Secondary poisoning of fish-eating birds and mammals is not likely to occur for cadmium at levels in water below the MAR calculated for aquatic ecosystems.
在制定环境质量标准时,二次中毒的效应评估有助于直接中毒的效应评估。本研究提出了一种二次中毒效应评估算法。以水-鱼-食鱼鸟类或哺乳动物途径为例分析了二次中毒途径。该算法中使用的参数是鱼类的生物富集因子(BCF)以及食鱼鸟类和哺乳动物组的无观测效应浓度(NOEC食鱼动物)。为了得出可靠的BCF,相较于基于定量构效关系(QSAR)的估算值,更倾向于使用实验得出的BCF。食鱼动物的NOEC是通过对单一物种的毒性数据进行外推得出的。由于食鱼物种的数据很少可得,因此使用了所有鸟类和哺乳动物物种的毒性数据。所提出的算法(MAR = NOEC食鱼动物/BCF)用于计算林丹、狄氏剂、镉、汞、多氯联苯153和多氯联苯118的最大可接受风险水平(MARS)。随后,通过将这些MARS与水生生物效应评估得出的MARS进行比较,得出结论:对于甲基汞和多氯联苯153,食鱼鸟类和哺乳动物的二次中毒可能是一条关键途径。对于这些化合物,在地表水浓度低于为水生生态系统计算的MAR时,就可能对食鱼鸟类和哺乳动物的种群产生影响。对于水中镉浓度低于为水生生态系统计算的MAR的情况,食鱼鸟类和哺乳动物不太可能发生二次中毒。