Department of Fisheries, Wildlife, and Conservation Biology, University of Minnesota, St. Paul, Minnesota 55108-6124, USA.
Environ Toxicol Chem. 2009 Oct;28(10):2216-23. doi: 10.1897/08-619.1.
Toxicity tests with ammonia, nitrite, and nitrate were conducted on the endangered Topeka shiner (Notropis topeka) to determine if current U.S. Environmental Protection Agency (U.S. EPA) water quality criteria are protective of this species. Results from acute lethal and chronic growth tests are reported for both Topeka shiners and fathead minnows (Pimephales promelas). Embryo-larval tests were conducted with only fathead minnows because Topeka shiner embryos were not available. Predicted outcomes for Topeka shiner embryo-larval toxicity endpoints were calculated by comparing relationships between growth tests and embryo-larval tests for fathead minnows and extrapolating those relationships to Topeka shiners. Results show that the U.S. EPA's criterion for total ammonia-nitrogen (TAN), 1.24 mg/L when early life stages are present, would be protective, given that our most sensitive result was a predicted maximum acceptable toxicant concentration (MATC) for Topeka shiners at 5.63 mg/L TAN, calculated from the fathead minnow chronic embryo-larval test. The U.S. EPA's criterion for nitrite (5 mg/L) would not be protective, given that our most sensitive result was a predicted MATC for Topeka shiners of 3.97 mg/L NO2-N, calculated from the fathead minnow chronic embryo-larval test. However, nitrite is generally transient, and unpublished field data show levels far lower than the criterion. Finally, the U.S. EPA's recommendation of a maximum of 90 mg/L NO3-N for the protection of warmwater fishes would protect Topeka shiners but not fathead minnows. For Topeka shiners, the MATC from the 30-d juvenile growth test was 360 mg/L NO3-N, but for fathead minnows, the MATC was 84 mg/L. More field sampling may be needed to determine if levels comply with criteria, especially in Topeka shiner critical habitat.
对濒危的托皮卡鲦鱼(Notropis topeka)进行了氨、亚硝酸盐和硝酸盐的毒性测试,以确定当前美国环境保护署(U.S. EPA)的水质标准是否能保护该物种。报告了托皮卡鲦鱼和黑头呆鱼(Pimephales promelas)的急性致死和慢性生长测试结果。仅用黑头呆鱼进行了胚胎-幼虫测试,因为没有托皮卡鲦鱼的胚胎。托皮卡鲦鱼胚胎-幼虫毒性终点的预测结果是通过比较黑头呆鱼生长测试和胚胎-幼虫测试之间的关系,并将这些关系外推到托皮卡鲦鱼来计算的。结果表明,美国环保署的总氨氮(TAN)标准为 1.24 毫克/升,当早期生命阶段存在时,这将是有保护作用的,因为我们最敏感的结果是托皮卡鲦鱼的最大允许毒物浓度(MATC)预测值为 5.63 毫克/升 TAN,这是从黑头呆鱼慢性胚胎-幼虫测试中计算出来的。美国环保署的亚硝酸盐(5 毫克/升)标准将没有保护作用,因为我们最敏感的结果是从黑头呆鱼慢性胚胎-幼虫测试中计算出的托皮卡鲦鱼的最大允许毒物浓度(MATC)预测值为 3.97 毫克/升 NO2-N。然而,亚硝酸盐通常是短暂的,未公布的现场数据显示,其水平远低于标准。最后,美国环保署建议最大硝酸盐氮含量为 90 毫克/升,以保护温水鱼类,这将保护托皮卡鲦鱼,但不保护黑头呆鱼。对于托皮卡鲦鱼,30 天幼鱼生长测试的 MATC 为 360 毫克/升 NO3-N,但对于黑头呆鱼,MATC 为 84 毫克/升。可能需要更多的现场采样来确定是否符合标准,特别是在托皮卡鲦鱼的关键栖息地。