ASTM E1850-04(2012)
水生和沉积物毒性试验中作为试验有机体的残留样品选择的标准指南

Standard Guide for Selection of Resident Species as Test Organisms for Aquatic and Sediment Toxicity Tests


ASTM E1850-04(2012) 发布历史

ASTM E1850-04(2012)由美国材料与试验协会 US-ASTM 发布于 2004。

ASTM E1850-04(2012) 发布之时,引用了标准

  • ASTM D4401 用彼得森抓斗取样器收集底栖大型无脊椎动物的标准实施规程
  • ASTM D4407 用桔皮抓斗取样器收集底栖大型无脊椎动物的标准实施规程
  • ASTM D4556 底栖大型无脊椎动物收集用流网取样装置标准指南
  • ASTM D4557 用苏伯尔和相关类型取样器收集底栖大型无脊椎动物的标准实施规程
  • ASTM D4558 用流网收集底栖大型无脊椎动物的标准实施规程
  • ASTM E1191 使用盐水水质进行生命周期毒性试验的标准指南
  • ASTM E1192 对鱼, 大型无脊椎动物和两栖动物的水环境样品和流出物进行剧毒毒性试验的标准指南
  • ASTM E1193 大型蚤生命周期毒性试验实施的标准指南
  • ASTM E1210 用亲水的乳化法作荧光液体渗透检验的试验方法
  • ASTM E1218 用微藻进行静态96小时毒性试验的标准指南
  • ASTM E1241 用鱼进行早期生命阶段毒性试验的标准指南
  • ASTM E1367 用海水中和河口处生长的端足类甲壳动物作10天静态沉淀物毒性试验
  • ASTM E1383 ASTM E1383-94a
  • ASTM E1415 用狐猴G3进行静态毒性试验的标准指南(2021年撤销)
  • ASTM E1440 短尾轮虫科剧毒性测试的标准指南
  • ASTM E1463 用美国西海岸糠虾目动物进行静态和无逆流急性毒性试验的标准指南
  • ASTM E1498 使用海藻进行有性繁殖试验的标准指南
  • ASTM E1525 设计用沉积物的生物试验
  • ASTM E1562 用多毛环节动物进行急性、慢性和生命周期水生毒性试验的标准指南
  • ASTM E1563 用海胆纲胚胎做静态剧毒试验的标准指南
  • ASTM E1611 用多毛环节动物进行沉积物毒性试验的标准指南
  • ASTM E1688 底栖无脊椎动物沉积物相关污染物生物累积性测定的标准指南
  • ASTM E1706 用淡水无脊椎动物测量沉积物相关污染物毒性的标准试验方法
  • ASTM E1913 在装有浸入式水生大型植物狐尾藻属SIBIRICUM蜀试验管里进行静态、无菌和14日植物性试验
  • ASTM E1924 生物荧光双鞭甲藻毒性试验的标准指南
  • ASTM E2122 用笼状双壳类进行现场生物测定的标准指南
  • ASTM E724 用四种咸水两瓣软疣幼虫进行静态急性毒力试验的标准指南
  • ASTM E729 用鱼, 大型无脊椎动物和两栖动物的试验用材料进行剧毒毒性试验的标准指南

ASTM E1850-04(2012)的历代版本如下:

  • 2019年 ASTM E1850-04(2019) 居民种类选择标准指南作为水生和沉积物毒性试验的试验生物
  • 2004年 ASTM E1850-04(2012) 水生和沉积物毒性试验中作为试验有机体的残留样品选择的标准指南
  • 2004年 ASTM E1850-04 居民种类选择标准指南作为水生和沉积物毒性试验的试验生物
  • 1997年 ASTM E1850-97 水生和沉积物毒性试验的试验有机体的残留样品选择的标准指南

 

5. Significance and UseTop Bottom

5.1 The USEPA's policy for whole-effluent monitoring stresses, an integrated approach to toxicity testing (1, 5) tests and other measures of toxicity, should be systematically employed and should be related to certain aquatic-system factors, such as the type of habitats available (benthic and water column), flow regime, and physicochemical quality of the site water and sediment. The determination of toxicity is generally accomplished with a few surrogate species for four major reasons: a regulatory agency can compare test results between sites and over time in order to help prioritize enforcement efforts, tests using these species are relatively inexpensive since the organisms can be cultured year-round under laboratory conditions, the reliability of test methods utilizing surrogate species is better established than for other species, and surrogate species are better integrated into toxicity identification evaluations than other species. For regulatory purposes, under the National Pollution Discharge Elimination System (NPDES), USEPA considers it unnecessary to conduct whole effluent toxicity tests with resident or indigenous species (6). An alternate testing procedure protocol is provided by USEPA for validating toxicity methods using species not already approved (6,7). In systems where surrogate species are not found, erroneous predictions might be obtained of environmental impact or water and sediment quality impairment based on toxicity tests using surrogate species (8).

5.2 This guide is intended to assist researchers and managers in selecting appropriate resident species for site-specific toxicity assessments. This guide could be used to select a resident species for use in predicting the potential toxic effects of a substance in certain types of aquatic environments. Another use might be for selecting a number of indigenous species from the aquatic community, that when tested, might indicate potential toxic effects of the test substance or material on the ecological integrity of that community. Selection of a suitable test species is very important because species might respond quite differently to toxic compounds (9). Species suggested as test organisms by regulatory agencies might not occur in the receiving waters of interest and their sensitivity to a toxic substance might not be representative of the sensitivity exhibited by resident species. Since aquatic ecosystem structure and function is often determined by a few key species (10, 11, 12, 13), toxicological......


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