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利用椭圆蚌对底特律河进行定量生物监测:1998年至2015年间水中多氯联苯稳态校正因子及时间趋势的验证

Quantitative Biomonitoring in the Detroit River Using Elliptio complanata: Verification of Steady State Correction Factors and Temporal Trends of PCBs in Water Between 1998 and 2015.

作者信息

Drouillard Ken G, Cook Mark, Leadley Todd A, Drca Paul, Briggs Ted, Haffner G Douglas

机构信息

Great Lakes Institute for Environmental Research (GLIER), University of Windsor, 401 Sunset Ave., Windsor, ON, N9B3P4, Canada.

Public Works Pollution Control Department, City of Windsor, 4155 Ojibway Parkway, Windsor, ON, N9C 4A5, Canada.

出版信息

Bull Environ Contam Toxicol. 2016 Dec;97(6):757-762. doi: 10.1007/s00128-016-1881-9. Epub 2016 Jul 6.

Abstract

Quantitative biomonitoring methods were applied to determine PCB concentrations in water from the Detroit River over a 17 year period. During 2014, mussels were deployed for and extended duration (21-364 days) and time dependent PCB concentrations were fit to a bioaccumulation model to estimate elimination coefficients (k) and provide site specific calibration of mussel toxicokinetics. The site specific calibration and different k versus K relationships from the literature were used to correct for steady state. ∑PCB concentrations in water were not significantly dependent on the k values used indicating that individual variation exceeds error contributed by steady state correction factors. The model was then applied to estimate ∑PCB concentrations in water using the long term (1998-2015) data. ∑PCBs concentrations in water exhibited a significant decreasing trend with a half life of 9.12 years resulting in a drop in yearly geometric mean residues from 198.1 to 43.6 pg/L.

摘要

采用定量生物监测方法,在17年的时间里测定底特律河水中的多氯联苯(PCB)浓度。2014年期间,贻贝被放置了较长时间(21 - 364天),并将随时间变化的PCB浓度拟合到生物累积模型中,以估计消除系数(k),并对贻贝的毒代动力学进行特定地点的校准。利用特定地点的校准以及文献中不同的k与K关系来校正稳态。水中的总多氯联苯(∑PCB)浓度与所使用的k值没有显著相关性,这表明个体差异超过了稳态校正因子所带来的误差。然后,该模型被应用于利用长期(1998 - 2015年)数据估计水中的∑PCB浓度。水中的∑PCBs浓度呈现出显著下降趋势,半衰期为9.12年,导致年几何平均残留量从198.1 pg/L降至43.6 pg/L。

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