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Rates of Microbial Transformation of Polycyclic Aromatic Hydrocarbons in Water and Sediments in the Vicinity of a Coal-Coking Wastewater Discharge

机译:焦化废水排放附近水和沉积物中多环芳烃的微生物转化率

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摘要

To facilitate predictions of the transport and fate of contaminants at future coal conversion facilities, rates of microbial transformation of polycyclic aromatic hydrocarbons were measured in stream water and sediment samples collected in the vicinity of a coal-coking treated wastewater discharge from November 1977 through August 1979. Six radiolabeled polycyclic aromatic hydrocarbons were incubated with sediment and water samples; 14CO2, cell-bound 14C, and polar transformation products were isolated and quantified. Whereas 14CO2 and bound 14C were major transformation products in sediment assays, soluble polar 14C dominated transformation in water samples. Mean rate constants (measured at 20°C) in sediments collected downstream from the effluent outfall were 7.8 × 10−2 h−1 (naphthalene), 1.6 × 10−2 h−1 (anthracene), and 3.3 × 10−3 h−1 [benz(a)anthracene], which corresponded to turnover times of 13, 62, and 300 h, respectively. No unequivocal evidence for transformation of benzo(a)pyrene or dibenz(a,h)anthracene was obtained. Only naphthalene and anthracene transformations were observed in water samples; rate constants were consistently 5- and 20-fold lower, respectively, than in the corresponding sediment samples. The measured rate constants for anthracene transformation in July 1978 sediment samples were not related to total heterotroph numbers. In late July 1978, the effluent was diverted from the primary study area; however, no differences were observed either in transformation rate constants or in the downstream/upstream sediment rate constant ratio. These results are consistent with the hypothesis that continuous inputs of polycyclic aromatic hydrocarbons result in an increased ability within a microbial community to utilize certain polycyclic aromatic hydrocarbons. However, because transformation rates remained elevated for more than 1 year after removal of the polycyclic aromatic hydrocarbon source, microbial communities may shift only slowly in response to changes in polycyclic aromatic hydrocarbon concentrations.
机译:为了便于预测未来煤炭转化设施中污染物的运输和结局,从1977年11月至1979年8月经煤焦化处理的废水排放附近收集的溪流水和沉积物样品中测量了多环芳烃的微生物转化率将六个放射性标记的多环芳烃与沉积物和水样品一起孵育;分离并定量了 14 CO2,细胞结合的 14 C和极性转化产物。在沉积物测定中, 14 CO2和结合的 14 C是主要的转化产物,而可溶性极性 14 C在水样中占主导。从出水口下游收集的沉积物中的平均速率常数(在20°C下测量)为7.8×10 −2 h -1 (萘),1.6×10 −2 h −1 (蒽)和3.3×10 −3 h -1 [苯并[a]蒽],分别对应13、62和300 h的周转时间。没有明确转化为苯并(a))或联苯(a,h)蒽的证据。在水样中仅观察到萘和蒽的转化。速率常数分别比相应的沉积物样品低5到20倍。 1978年7月沉积物样品中蒽转化率的测量常数与总异养菌数无关。 1978年7月下旬,污水从主要研究区转移。然而,无论是转化速率常数还是下游/上游沉积物速率常数比都没有发现差异。这些结果与以下假设一致:多环芳烃的连续输入导致微生物群落内利用某些多环芳烃的能力增强。但是,由于去除多环芳烃源后转化率在一年多的时间内仍保持升高,因此微生物群落可能仅响应多环芳烃浓度的变化而缓慢变化。

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