首页> 外文期刊>Environmental toxicology and chemistry >MODELING METAL BIOACCUMULATION AND TISSUE DISTRIBUTION IN KILLIFISH (FUNDULUS HETEROCLITUS) IN THREE CONTAMINATED ESTUARIES
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MODELING METAL BIOACCUMULATION AND TISSUE DISTRIBUTION IN KILLIFISH (FUNDULUS HETEROCLITUS) IN THREE CONTAMINATED ESTUARIES

机译:在三种污染的河口中模拟奇异果(真菌异种)中金属的生物累积和组织分布

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The present study experimentally assessed the uptake, loss, and resulting tissue distribution of As(V), Cd. Cr(Ⅲ), Hg(Ⅱ), and methylmercury (MeHg) in killifish (Fundulus heteroclitus) following aqueous exposure in water collected from 3 contaminated field sites-Baltimore Harbor and Elizabeth River (Chesapeake Bay), and Mare Island (San Francisco Bay)—using a radiotracer technique. Uptake rate constants (Lg~(-1) d~(-1)) were highest for MeHg (0.370-0.781) and lowest for As (0.00028-0.0006.). Loss rate constants (d~(-1)) were highest for As (0.046-0.096) and lowest for MeHg (0.006-0.009). Tissue distribution data showed that MeHg was redistributed around the body throughout the 9-d depuration period, and drinking may be an uptake mechanism for Cd from the aqueous phase in higher-salinity water. The kinetic parameters calculated in the present study were entered into a bioaccumulation model to calculate the predicted body burden of each metal at steady state and the percentage body burden attributable to dietary exposure on a site-specific basis. Calculated body burdens varied between field sites for all metals except Cr. The predicted values for Cd, Hg(Ⅱ), and MeHg matched independent field data from contaminated estuaries, indicating that the model can account for the major processes governing metal concentration in killifish. The diet accounted for >97% of the body burden of Cd and MeHg and was the predominant exposure route for As and Cr.
机译:本研究通过实验评估了As(V),Cd的吸收,损失和组织分布。从三个受污染的场址巴尔的摩港和伊丽莎白河(切萨皮克湾)以及马雷岛(旧金山湾)收集的水中接触后,在奇异鱼(Fundulus heteroclitus)中,水中的Cr(Ⅲ),Hg(Ⅱ)和甲基汞(MeHg) )-使用放射性示踪剂技术。 MeHg的吸收速率常数(Lg〜(-1)d〜(-1))最高(0.370-0.781),而As最低(0.00028-0.0006。)。砷的损耗率常数(d〜(-1))最高(0.046-0.096),甲基汞的损耗率常数最低(0.006-0.009)。组织分布数据表明,在整个9天的净化期间,MeHg在体内重新分布,并且饮用可能是高盐度水中水相中Cd的吸收机制。将本研究中计算出的动力学参数输入到生物蓄积模型中,以在特定位置计算每种金属在稳态下的预测人体负荷以及可归因于饮食的身体负荷百分比。对于场外场所,除铬以外的所有金属的计算得出的人体负担都不同。 Cd,Hg(Ⅱ)和MeHg的预测值与受污染河口的独立场数据相匹配,表明该模型可以解释控制鱼类中主要金属浓度的主要过程。饮食占人体Cd和MeHg负担的> 97%,是As和Cr的主要暴露途径。

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