Doig Lorne E, Liber Karsten
Toxicology Centre, 44 Campus Drive, University of Saskatchewan, Saskatoon, Sask., Canada S7N 5B3.
Ecotoxicol Environ Saf. 2007 Feb;66(2):169-77. doi: 10.1016/j.ecoenv.2005.12.011. Epub 2006 Feb 23.
This study evaluated nickel (Ni) speciation in the presence of different fractions (humic acid (HA), fulvic acid (FA)) and sources (natural sediment, Suwannee River, peat moss) of dissolved organic matter (DOM) at Ni concentrations toxicologically relevant to the freshwater amphipod, Hyalella azteca. The free Ni ion, Ni(2+), was measured in reconstituted water (with or without DOM) using a miniaturized ion-exchange technique (IET). Ni speciation from these experiments was compared to calculated results obtained from equilibrium modelling (WHAM, Model VI). While it is known that Ni will complex with DOM, it was found that under acutely toxic Ni exposure concentrations ([Ni(Total)]=5mg/L, or 85.1 microM) representative surface-water DOC concentrations ( approximately 10mg/L) played little or no role in Ni speciation. Conversely, at sublethal Ni exposure concentrations ([Ni(Total)]=0.2 and 0.5 microg/L, or 3.4 and 8.51 microM, respectively) DOM significantly affected Ni speciation with [Ni(2+)] decreasing with increasing concentration of DOM. It was found that for similar concentrations of DOC (same fraction, different sources), the measured Ni(2+) concentrations were reduced (relative to the control), but similar to one another. Conversely, at similar DOC concentrations, the HA fraction reduced Ni(2+) levels to a greater extent than the associated FA fraction. Overall, this study provides proof of principle that Suwannee River and peat humic substances are suitable analogues for natural sediment pore-water DOM when evaluating Ni bioavailability in freshwater.
本研究评估了在与淡水双足类动物阿氏摇蚊毒理学相关的镍(Ni)浓度下,不同组分(腐殖酸(HA)、富里酸(FA))和溶解有机物(DOM)来源(天然沉积物、苏万尼河、泥炭藓)存在时镍的形态。使用小型离子交换技术(IET)在重构水中(有或无DOM)测量游离镍离子Ni(2+)。将这些实验得到的镍形态与通过平衡模型(WHAM,模型VI)获得的计算结果进行比较。虽然已知镍会与DOM络合,但发现在急性毒性镍暴露浓度([Ni(总量)]=5mg/L,或85.1μM)下,代表性地表水DOC浓度(约10mg/L)在镍形态形成中作用很小或没有作用。相反,在亚致死镍暴露浓度([Ni(总量)]分别为0.2和0.5μg/L,或3.4和8.51μM)下,DOM显著影响镍形态,[Ni(2+)]随DOM浓度增加而降低。结果发现,对于类似浓度的DOC(相同组分,不同来源),测量的Ni(2+)浓度降低(相对于对照),但彼此相似。相反,在类似DOC浓度下,HA组分比相关的FA组分更大程度地降低Ni(2+)水平。总体而言,本研究提供了原理证明,即在评估淡水中镍的生物可利用性时,苏万尼河和泥炭腐殖物质是天然沉积物孔隙水DOM的合适类似物。