ORD/CEMM Atlantic Coastal Environmental Sciences Division, US Environmental Protection Agency, Narragansett, Rhode Island.
Harvard T. H. Chan School of Public Health, Boston, Massachusetts, USA.
Environ Toxicol Chem. 2023 Feb;42(2):317-332. doi: 10.1002/etc.5536. Epub 2023 Jan 13.
Biomonitoring at contaminated sites undergoing cleanup, including Superfund sites, often uses bioaccumulation of anthropogenic contaminants by field-deployed organisms as a metric of remedial effectiveness. Bioaccumulation studies are unable to assess the equilibrium status of the organisms relative to the contaminants to which they are exposed. Establishing equilibrium provides a reproducible benchmark on which scientific and management decisions can be based (e.g., comparison with human dietary consumption criteria). Unlike bioaccumulating organisms, passive samplers can be assessed for their equilibrium status. In our study, over a 3-year period, we compared the bioaccumulation of selected polychlorinated biphenyls (PCBs) by mussels in water column deployments at the New Bedford Harbor Superfund site (New Bedford, MA, USA) to codeployed passive samplers. Based on comparisons to the calculated passive sampler equilibrium concentrations, the mussels were not at equilibrium, and the subsequent analysis focused on evaluating approaches for estimating equilibrium bioaccumulation. In addition, a limited evaluation of metal bioaccumulation by the exposed mussels and a metal passive sampler was performed. In general, mussel and passive sampler accumulation of PCBs was significantly correlated; however, surprisingly, agreement on the magnitude of accumulation was optimal when bioaccumulation and passive sampler uptake were not corrected for nonequilibrium conditions. A subsequent comparison of four approaches for estimating equilibrium mussel bioaccumulation using octanol-water partition coefficients (K ), triolein-water partition coefficients (K ), and two types of polymer-lipid partition coefficients demonstrated that field-deployed mussels were not at equilibrium with many PCBs. A range of estimated equilibrium mussel bioaccumulation concentrations were calculated, with the magnitude of the K -based values being the smallest and the polymer-lipid partition coefficient-based values being the largest. These analyses are intended to assist environmental scientists and managers to interpret field deployment data when transitioning from biomonitoring to passive sampling. Environ Toxicol Chem 2023;42:317-332. Published 2022. This article is a U.S. Government work and is in the public domain in the USA.
在受污染场地(包括超级基金场地)进行清理时,生物监测通常使用现场部署的生物体对人为污染物的生物积累作为补救有效性的指标。生物积累研究无法评估生物体相对于其暴露的污染物的平衡状态。建立平衡状态为科学和管理决策提供了可重复的基准(例如,与人类膳食消费标准进行比较)。与生物积累的生物体不同,被动采样器可以评估其平衡状态。在我们的研究中,在 3 年的时间里,我们将新贝德福德港超级基金场地(美国马萨诸塞州新贝德福德)水柱状部署的贻贝对选定多氯联苯 (PCB) 的生物积累与同时部署的被动采样器进行了比较。基于与计算出的被动采样器平衡浓度的比较,贻贝未达到平衡状态,随后的分析重点是评估估计平衡生物积累的方法。此外,还对暴露贻贝和金属被动采样器的金属生物积累进行了有限评估。一般来说,贻贝和被动采样器对 PCB 的积累呈显著相关性;然而,令人惊讶的是,当不对非平衡条件进行生物积累和被动采样器摄取校正时,对积累量的一致性最佳。随后,使用辛醇-水分配系数 (Kow)、三油酸-水分配系数 (Kow) 和两种类型的聚合物-脂质分配系数比较了四种估计平衡贻贝生物积累的方法,结果表明现场部署的贻贝与许多 PCB 未达到平衡状态。计算了一系列估计的平衡贻贝生物积累浓度,基于 Kow 的值最小,聚合物-脂质分配系数的值最大。这些分析旨在帮助环境科学家和管理者在从生物监测过渡到被动采样时解释现场部署数据。环境毒理化学 2023;42:317-332。2022 年出版。本文是美国政府的工作,在美国属于公有领域。