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Enhanced kinetics of solid-phase microextraction and biodegradation of polycyclic aromatic hydrocarbons in the presence of dissolved organic matter

机译:溶解有机物存在下多环芳烃固相微萃取和生物降解的动力学增强

摘要

The uptake kinetics of fluorene, phenanthrene, fluoranthene, pyrene, and benzo[e]pyrene by solid-phase microextraction fibers was studied in the presence of dissolved organic matter (DOM) obtained from sediment pore water and resulted in increased fiber absorption and desorption rate coefficients. Compared to the control without DOM, these rate coefficients were increased at a DOM concentration of 36.62 mg/L by a factor of 1.27 to 2.21 and 1.31 to 2.10 for fluorene and benzo[e]pyrene, respectively. The calculated values for the fiber absorption and desorption rate coefficients show that diffusion through an unstirred boundary layer (UBL) surrounding the fiber probably forms the rate-limiting step of the process. The mineralization of aqueous-phase phenanthrene and pyrene by a representative polycyclic aromatic hydrocarbon (PAH)-degrading bacterium (Mycobacterium gilvum VM552) also was found to be enhanced by DOM. The initial degradation rates of phenanthrene (9.03 μg/L) and pyrene (1.96 μg/L) were significantly higher compared to the control values and were enhanced by a factor of 1.32 and 1.26 at a DOM concentration of 43.14 and 42.15 mg/L, respectively. We suggest that such an enhancement results from the combination of faster uptake kinetics of the water-dissolved compounds in the UBL surrounding microbial cells and direct access of the bacteria to DOM-associated PAHs. These enhanced kinetic effects of DOM may have strong implications in sediment processes like desorption, nonequilibrium exposure, and biodegradation.
机译:研究了固相微萃取纤维在沉积物孔隙水中获得溶解有机物(DOM)的情况下,通过固相微萃取纤维对芴,菲,荧蒽,pyr和苯并[e] up的吸收动力学,从而提高了纤维的吸收和解吸速率系数。与没有DOM的对照相比,芴和苯并[e] py的DOM浓度为36.62 mg / L时,这些速率系数分别提高了1.27至2.21和1.31至2.10倍。纤维吸收和解吸速率系数的计算值表明,通过围绕纤维的未搅拌边界层(UBL)扩散可能会形成该过程的速率限制步骤。 DOM还发现了代表性的降解多环芳烃(PAH)的细菌(gilcoum gilvum VM552)对水相菲和pyr的矿化作用。菲(9.03μg/ L)和pyr(1.96μg/ L)的初始降解率比对照值高得多,并且在DOM浓度为43.14和42.15 mg / L时,降解率分别提高了1.32和1.26,分别。我们认为,这种增强作用是由于UBL周围微生物细胞中水溶性化合物的更快吸收动力学和细菌直接与DOM相关的PAHs结合而产生的。 DOM的这些增强的动力学效应可能会对诸如解吸,非平衡暴露和生物降解的沉积过程产生重大影响。

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