US Geological Survey, Columbia Environmental Research Center, Columbia, Missouri, USA.
Environ Toxicol Chem. 2013 Nov;32(11):2482-94. doi: 10.1002/etc.2272. Epub 2013 Aug 6.
Two spiking methods were compared and nickel (Ni) partitioning was evaluated during a series of toxicity tests with 8 different freshwater sediments having a range of physicochemical characteristics. A 2-step spiking approach with immediate pH adjustment by addition of NaOH at a 2:1 molar ratio to the spiked Ni was effective in producing consistent pH and other chemical characteristics across a range of Ni spiking levels. When Ni was spiked into sediment having a high acid-volatile sulfide and organic matter content, a total equilibration period of at least 10 wk was needed to stabilize Ni partitioning. However, highest spiking levels evidently exceeded sediment binding capacities; therefore, a 7-d equilibration in toxicity test chambers and 8 volume-additions/d of aerobic overlying water were used to avoid unrealistic Ni partitioning during toxicity testing. The 7-d pretest equilibration allowed excess spiked Ni and other ions from pH adjustment to diffuse from sediment porewater and promoted development of an environmentally relevant, 0.5- to 1-cm oxic/suboxic sediment layer in the test chambers. Among the 8 different spiked sediments, the logarithm of sediment/porewater distribution coefficient values (log Kd ) for Ni during the toxicity tests ranged from 3.5 to 4.5. These Kd values closely match the range of values reported for various field Ni-contaminated sediments, indicating that testing conditions with our spiked sediments were environmentally realistic.
两种加标方法进行了比较,并在一系列毒性测试中评估了镍(Ni)的分配情况,这些测试使用了 8 种具有不同物理化学特性的淡水沉积物。采用两步加标法,即用 2:1 的摩尔比将 NaOH 加入到加标 Ni 中立即调整 pH 值,可有效在一系列 Ni 加标水平下保持一致的 pH 值和其他化学特性。当 Ni 被加入到具有高酸可挥发性硫化物和有机质含量的沉积物中时,需要至少 10 周的总平衡期才能稳定 Ni 的分配。然而,最高加标水平显然超过了沉积物的结合能力;因此,在毒性测试室中进行了 7 天的预平衡期,并每天添加 8 倍体积的好氧上层水,以避免在毒性测试过程中出现不现实的 Ni 分配。7 天的预平衡期允许过量的加标 Ni 和其他来自 pH 值调整的离子从沉积物孔隙水中扩散出来,并促进了在测试室中形成一个与环境相关的、0.5 到 1 厘米厚的好氧/缺氧沉积物层。在 8 种不同的加标沉积物中,毒性测试过程中 Ni 的沉积物/孔隙水分配系数(logKd)值范围从 3.5 到 4.5。这些 Kd 值与各种野外受 Ni 污染沉积物的报告值范围非常匹配,表明我们使用加标沉积物的测试条件具有实际的环境意义。