首页> 外文期刊>Archives of Environmental Contamination and Toxicology >Determination of toxicokinetic parameters for bioconcentration of water-soluble fraction of petroleum hydrocarbon associated with no. 0 diesel in Changjiang estuary and Jiaozhou bay: model versus mesocosm experiments.
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Determination of toxicokinetic parameters for bioconcentration of water-soluble fraction of petroleum hydrocarbon associated with no. 0 diesel in Changjiang estuary and Jiaozhou bay: model versus mesocosm experiments.

机译:测定与No.4相关的石油烃水溶性馏分的生物浓缩的毒物动力学参数0长江口和胶州湾的柴油:模型与中观试验。

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摘要

A method is proposed for determination of toxicokinetic parameters for bioconcentration by phytoplankton of the water-soluble fraction (WSF) of petroleum hydrocarbon (PH) associated with No. 0 diesel, in which WSF-PH concentration in phytoplankton cells, C(A(d)), is estimated by subtracting concentration in water (S-bottle) containing a phytoplankton sample from that in a C-bottle without phytoplankton. It was demonstrated that C(A(d)) agrees well with the concentration found by direct ultrasonication extraction of collected cells, C(A(ind)) ( r = 0.88, p < 0.0001), and its uncertainty was about 17.6%. Mesocosms in 25-m3 ethylene vinyl acetate or 4-m3 polyethylene bags were performed at two sites in China: Changjiang Estuary in spring/summer 1998 and Jiaozhou Bay in autumn 1999 and spring/summer 2000. The experiments were designed to determine toxicokinetic parameters, including specific rates of uptake and elimination, and bioconcentration factor (BCF), for bioconcentration of WSF-PH by phytoplankton. A modified kinetic two-compartment model for bioconcentration of WSF-PH by phytoplankton was developed to estimate the toxicokinetic parameters. In the model, the influence of phytoplankton growth on bioconcentration and WSF-PH decline due to biotic and abiotic processes other than bioconcentration, such as volatilization, microbial degradation, phytolysis, and sorption expressed as an exponential-decay equation, are taken into account. Size-dependent BCF was observed in the laboratory experiment. BCFs were 1.0 x 10(4) in summer in Changjiang Estuary, 1.6 x 10(4) in summer, and 1.1 x 10(4) in autumn in Jiaozhou Bay. The difference in BCF may be interpreted by its size dependence.
机译:提出了一种通过浮游植物确定与0号柴油相关的石油烃(PH)的水溶性级分(WSF)的生物浓缩毒性动力学参数的方法,其中浮游植物细胞中的WSF-PH浓度为C(A(d ))是通过从无浮游植物的C瓶中减去含有浮游植物样品的水(S瓶)中的浓度来估算的。结果表明,C(A(d))与直接超声提取收集到的细胞的浓度C(A(ind))非常吻合(r = 0.88,p <0.0001),不确定度约为17.6%。在中国的两个地点进行了25 m3乙烯乙酸乙烯酯袋或4-m3聚乙烯袋的中膜清洗:1998年春夏季的长江口,1999年秋季和2000年春夏季的胶州湾。这些实验旨在确定毒物动力学参数,包括浮游植物对WSF-PH的生物富集的具体吸收和消除速率以及生物富集因子(BCF)。建立了用于浮游植物生物富集WSF-PH的改进的动力学两室模型,以估算毒代动力学参数。在该模型中,考虑了浮游植物生长对生物浓度和WSF-PH下降的影响,这是由于生物富集,微生物降解,植物分解和吸附等生物浓缩以外的生物过程和非生物过程引起的,而生物浓缩过程是以指数衰减方程表示的。在实验室实验中观察到大小依赖性的BCF。长江口夏季的BCF为夏季的1.0 x 10(4),夏季为胶州湾的夏季为1.6 x 10(4),秋季为1.1 x 10(4)。 BCF的差异可以通过其大小依赖性来解释。

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