Nys Charlotte, Janssen Colin R, De Schamphelaere Karel A C
Faculty of Bioscience Engineering, GhenToxLab, Ghent University, Coupure Links 653, B-9000 Ghent, Belgium.
Environ Pollut. 2017 Jan;220(Pt B):1271-1281. doi: 10.1016/j.envpol.2016.10.104. Epub 2016 Nov 9.
Recently, several bioavailability-based models have been shown to predict acute metal mixture toxicity with reasonable accuracy. However, the application of such models to chronic mixture toxicity is less well established. Therefore, we developed in the present study a chronic metal mixture bioavailability model (MMBM) by combining the existing chronic daphnid bioavailability models for Ni, Zn, and Pb with the independent action (IA) model, assuming strict non-interaction between the metals for binding at the metal-specific biotic ligand sites. To evaluate the predictive capacity of the MMBM, chronic (7d) reproductive toxicity of Ni-Zn-Pb mixtures to Ceriodaphnia dubia was investigated in four different natural waters (pH range: 7-8; Ca range: 1-2 mM; Dissolved Organic Carbon range: 5-12 mg/L). In each water, mixture toxicity was investigated at equitoxic metal concentration ratios as well as at environmental (i.e. realistic) metal concentration ratios. Statistical analysis of mixture effects revealed that observed interactive effects depended on the metal concentration ratio investigated when evaluated relative to the concentration addition (CA) model, but not when evaluated relative to the IA model. This indicates that interactive effects observed in an equitoxic experimental design cannot always be simply extrapolated to environmentally realistic exposure situations. Generally, the IA model predicted Ni-Zn-Pb mixture toxicity more accurately than the CA model. Overall, the MMBM predicted Ni-Zn-Pb mixture toxicity (expressed as % reproductive inhibition relative to a control) in 85% of the treatments with less than 20% error. Moreover, the MMBM predicted chronic toxicity of the ternary Ni-Zn-Pb mixture at least equally accurately as the toxicity of the individual metal treatments (RMSE = 16; RMSE = 18; RMSE = 17; RMSE = 23). Based on the present study, we believe MMBMs can be a promising tool to account for the effects of water chemistry on metal mixture toxicity during chronic exposure and could be used in metal risk assessment frameworks.
最近,已证明几种基于生物利用度的模型能够以合理的准确度预测急性金属混合物毒性。然而,此类模型在慢性混合物毒性方面的应用尚不完善。因此,在本研究中,我们通过将现有的针对镍、锌和铅的慢性水蚤生物利用度模型与独立作用(IA)模型相结合,开发了一种慢性金属混合物生物利用度模型(MMBM),假定金属在特定金属的生物配体位点结合时不存在相互作用。为了评估MMBM的预测能力,在四种不同的天然水体(pH范围:7 - 8;钙范围:1 - 2 mM;溶解有机碳范围:5 - 12 mg/L)中研究了镍 - 锌 - 铅混合物对 dubia 角突网纹溞的慢性(7天)生殖毒性。在每种水体中,以等毒性金属浓度比以及环境(即实际)金属浓度比研究混合物毒性。混合物效应的统计分析表明,相对于浓度相加(CA)模型进行评估时,观察到的交互效应取决于所研究的金属浓度比,但相对于IA模型进行评估时则不然。这表明在等毒性实验设计中观察到的交互效应不能总是简单地外推到环境实际暴露情况。一般来说,IA模型比CA模型更准确地预测了镍 - 锌 - 铅混合物毒性。总体而言,MMBM在85%的处理中预测镍 - 锌 - 铅混合物毒性(相对于对照表示为生殖抑制百分比)的误差小于20%。此外,MMBM预测三元镍 - 锌 - 铅混合物的慢性毒性至少与单个金属处理的毒性一样准确(均方根误差分别为16、18、17、23)。基于本研究,我们认为MMBM可能是一种很有前景的工具,可用于解释水化学对慢性暴露期间金属混合物毒性的影响,并可用于金属风险评估框架。