Great Lakes Institute for Environmental Research (GLIER), University of Windsor, Windsor, Ontario, Canada.
Department of Civil, Geological & Environmental Engineering, University of Saskatchewan, Saskatoon, Saskatchewan, Canada.
Integr Environ Assess Manag. 2019 May;15(3):398-411. doi: 10.1002/ieam.4130. Epub 2019 Mar 5.
Contaminant remediation decisions often focus on sediment-organism relationships, omitting the partitioning between sediment and water that exists across a given site. The present study highlights the importance of incorporating nonsedimentary routes of exposure into a nonequilibrium, steady-state food web bioaccumulation model for predicting polychlorinated biphenyl (PCB) concentrations in benthic invertebrates. Specifically, we examined the proportion of overlying water relative to the sediment porewater respired by benthic invertebrates, which has been used in previous studies to examine contaminant bioaccumulation. We evaluated the model accuracy using paired benthos-sediment samples and an extensive fish contamination database to ensure realistic predictions at the base of the Detroit River (Ontario, Canada, and Michigan, USA) food web. The results demonstrate that, compared with empirical regression analyses, the food web bioaccumulation model provided satisfactory estimates of PCB bioaccumulation for benthos simulations and better estimates for fish simulations. Our results showed that PCB bioaccumulation measurements are significantly affected by variations in pollutant uptake and elimination routes via the overlying water, which in turn are affected by the degree of disequilibrium of PCBs between sediments and water. Interestingly, we obtained contrasting results regarding the effectiveness of remediation strategies for reducing the contaminant burden of the aquatic biota based on different proportions of overlying water relative to porewater. These differences could consequently impact decisions about the approaches for source control and strategic sediment remediation. This study suggests that bioaccumulation assessments could be improved through better identification of chemical uptake-elimination routes in benthos and by accounting for chemical bioavailability in sediment and water components in areas with disequilibrium.Integr Environ Assess Manag 2019;00:000-000. © 2019 SETAC.
污染物修复决策通常侧重于沉积物-生物关系,而忽略了给定地点存在的沉积物与水之间的分配。本研究强调了将非沉积暴露途径纳入非平衡稳态食物网生物累积模型的重要性,以预测底栖无脊椎动物中多氯联苯(PCB)的浓度。具体而言,我们研究了底栖无脊椎动物呼吸的上覆水相对于沉积物孔隙水的比例,这在以前的研究中被用来研究污染物的生物累积。我们使用配对的底栖生物-沉积物样本和广泛的鱼类污染数据库来评估模型的准确性,以确保在底特律河(加拿大安大略省和美国密歇根州)食物网的基础上进行现实的预测。结果表明,与经验回归分析相比,食物网生物累积模型为底栖生物模拟提供了令人满意的 PCB 生物累积估计值,为鱼类模拟提供了更好的估计值。我们的结果表明,PCB 生物累积测量值受到通过上覆水的污染物吸收和消除途径变化的显著影响,而这又受到 PCB 在沉积物和水中的非平衡程度的影响。有趣的是,我们根据上覆水与孔隙水的不同比例,获得了关于修复策略降低水生生物群污染物负担的有效性的相反结果。这些差异可能会影响关于源控制和战略沉积物修复方法的决策。本研究表明,通过更好地确定底栖生物化学吸收-消除途径,并考虑到沉积物和水中化学物质的生物可利用性,可以改善生物累积评估在非平衡地区。