Columbia Environmental Research Center, US Geological Survey, Columbia, Missouri.
Water Quality Branch, US Environmental Protection Agency, Chicago, Illinois.
Environ Toxicol Chem. 2020 Nov;39(11):2256-2268. doi: 10.1002/etc.4841. Epub 2020 Sep 16.
The US Environmental Protection Agency (USEPA) is reviewing the protectiveness of the national ambient water quality criteria (WQC) for nickel (Ni) and zinc (Zn) and compiling toxicity databases to update the WQC. An amphipod (Hyalella azteca) and a unionid mussel (Lampsilis siliquoidea) have shown high sensitivity to Ni and Zn in previous studies. However, there remained uncertainties regarding the influence of test duration (48 vs 96 h) and the presence and absence of food in acute exposures with the amphipod, and there were also concerns about poor control of amphipod growth and reproduction and mussel growth in chronic exposures. We conducted acute 48- and 96-h water-only toxicity tests to evaluate the influence of feeding and test durations on the toxicity of dissolved Ni and Zn to the amphipod; we also used recently refined test methods to conduct chronic Ni and Zn toxicity tests to evaluate the sensitivity of the amphipod (6-wk exposure) and the mussel (4- and 12-wk exposures). The 96-h 50% effect concentrations (EC50s) of 916 µg Ni/L and 99 µg Zn/L from acute amphipod tests without feeding decreased from the 48-h EC50s by 62 and 33%, respectively, whereas the 96-h EC50s of 2732 µg Ni/L and 194 µg Zn/L from the tests with feeding decreased from the 48-h EC50s by 10 and 26%, indicating that the presence or absence of food had apparent implications for the 96-h EC50. Our chronic 6-wk EC20s for the amphipod (4.5 µg Ni/L and 35 µg Zn/L) were 50 to 67% lower than the 6-wk EC20s from previous amphipod tests, and our chronic 4-wk EC20s for the mussel (41 µg Ni/L and 66 µg Zn/L) were similar to or up to 42% lower than the 4-wk EC20s from previous mussel tests. The lower EC20s from the present study likely reflect more accurate estimates of inherent sensitivity to Ni and Zn due to the refined test conditions. Finally, increasing the chronic test duration from 4 to 12 wk substantially increased the toxicity of Zn to the mussel, whereas the 4- and 12-wk Ni effect needs to be re-evaluated to understand the large degree of variation in organism responses observed in the present study. Environ Toxicol Chem 2020;39:2256-2268. © 2020 SETAC.
美国环境保护署(USEPA)正在审查镍(Ni)和锌(Zn)的国家环境水质标准(WQC)的保护效力,并编制毒性数据库以更新 WQC。在之前的研究中,两种甲壳类动物(Hyalella azteca)和贻贝类(Lampsilis siliquoidea)对 Ni 和 Zn 表现出很高的敏感性。然而,在甲壳类动物的急性暴露中,测试持续时间(48 小时与 96 小时)和是否有食物存在的影响仍然存在不确定性,并且还存在对甲壳类动物生长和繁殖以及贻贝类生长的慢性暴露的控制不佳的担忧。我们进行了 48 小时和 96 小时的纯水质急性毒性测试,以评估喂养和测试持续时间对溶解 Ni 和 Zn 对甲壳类动物毒性的影响;我们还使用最近改进的测试方法进行了慢性 Ni 和 Zn 毒性测试,以评估甲壳类动物(6 周暴露)和贻贝类(4 周和 12 周暴露)的敏感性。无喂养的甲壳类动物急性测试中 96 小时 50%效应浓度(EC50)为 916μg/L 的 Ni 和 99μg/L 的 Zn,分别比 48 小时 EC50 低 62%和 33%,而有喂养的甲壳类动物急性测试中 96 小时 EC50 为 2732μg/L 的 Ni 和 194μg/L 的 Zn,分别比 48 小时 EC50 低 10%和 26%,表明有无食物对 96 小时 EC50 有明显影响。我们的甲壳类动物慢性 6 周 EC20(4.5μg/L 的 Ni 和 35μg/L 的 Zn)比之前甲壳类动物测试的 6 周 EC20 低 50%至 67%,而我们的贻贝类慢性 4 周 EC20(41μg/L 的 Ni 和 66μg/L 的 Zn)与之前贻贝类测试的 4 周 EC20 相似或低 42%。本研究中较低的 EC20 可能反映了由于测试条件的改进,对 Ni 和 Zn 的固有敏感性的更准确估计。最后,将慢性测试时间从 4 周延长至 12 周,显著增加了 Zn 对贻贝类的毒性,而需要重新评估 4 周和 12 周的 Ni 效应,以了解本研究中观察到的生物体反应的很大程度的变化。环境毒理化学 2020;39:2256-2268。 © 2020 SETAC。