In vitro digestive fluid extraction as a measure of the bioavailability of sediment‐associated polycyclic aromatic hydrocarbons: Sources of variation and implications for partitioning models
In vitro digestive fluid extraction as a measure of the bioavailability of sediment‐associated polycyclic aromatic hydrocarbons: Sources of variation and implications for partitioning models
复制标题
体外消化液提取作为沉积物相关多环芳烃生物利用度的衡量标准:变异来源和对分配模型的影响
DOI:
10.1002/etc.5620170509
复制
发表时间:
1998
影响因子:
4.1
通讯作者:
L. Mayer
中科院分区:
文献类型:
--
作者:
D. Weston;L. Mayer
In vitro extraction of contaminated sediments using the digestive fluid of a deposit‐feeding polychaete has recently been proposed to study contaminant bioaccumulation mechanisms and perhaps to better quantify the bioavailable contaminant fraction. This approach was evaluated using digestive fluid from the polychaete Arenicola brasiliensis and six marine sediments containing both spiked radiolabeled polycyclic aromatic hydrocarbons (PAHs) and in situ–contaminated unlabeled PAHs. The proportion of total contaminant extracted by digestive fluid from each sediment varied from 22 to 71% and 13 to 52%, for phenanthrene and benzo[a]pyrene, respectively. The proportions of contaminant solubilized were inversely correlated with the sediments' organic carbon content. The extent of PAH solubilization among sediments by A. brasiliensis digestive fluid was highly correlated with that of digestive fluid from the echiuran Urechis caupo and appears to be a consequence of surfactant properties of the fluids rather than of their enzymatic activity. The proportion of PAHs solubilized in vitro was similar to in vivo measurements of solubilization for contaminant exposures lasting about 24 h. However, with continued exposure, in vivo PAH concentrations in the digestive fluid increased fivefold, suggesting that digestive fluid is retained in the gut longer than sediment and thus accumulates PAHs through sequential digestion of many gut volumes. This phenomenon may enhance contaminant fugacity in the gut and increase the potential for bioaccumulation or toxicity.