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首页> 外文期刊>Water Research >BIODEGRADATION OF POLYAROMATIC HYDROCARBONS BY MARINE BACTERIA EFFECT OF SOLID PHASE ON DEGRADATION KINETICS
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BIODEGRADATION OF POLYAROMATIC HYDROCARBONS BY MARINE BACTERIA EFFECT OF SOLID PHASE ON DEGRADATION KINETICS

机译:固相对降解动力学的海洋细菌生物降解多溴代烃

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摘要

Biodegradation kinetics for phenanthrene and fluoranthene, as a function of their dissolved concentrations, were determined for a marine PAH-degrading enrichment. Biodegradation rates in the presence of artificial (Celite coated with humic acid) or Puget Sound sediments with sorbed PAH were then determined. These rates were expected to be slower than for the tests without sediment, because of limited PAH in the soluble phase due to desorption limitations of PAH from the solid to liquid phases. Due to the low aqueous PAH concentrations that exist for PAH compounds, radiolabeled PAH com- pounds were used to follow the fate of the PAH compounds in batch degradation test. The radiolabeled compounds were followed as evolved CO2, unreacted PAH in the dissolved phase or sorbed to sedi- ment, and as non-polar intermediate products. Epifluorescence microscopy was used to determine if the manne enrichment bacteria could attach to sediment during PAH degradation. Without sediment, first- order degradation rate coefficients with respect to PAH concentration for phenanthrene ranged from 0.033 to 0.139 L/mg-d, depending on when the marine enrichment was tested. Fluoranthene first-order degradation rate coefficients without sediment were 0.132 and 0.162 L/mg-d. With sediment present, degradation rates for phenanthrene and fluoranthene were 2.1 to 3.5 and 2.1 to 5.3 times faster,respect- ively, than the degradation rates at the same aqueous PAH and biomass concentrations without sedi- ment. With phenanthrene present about 50 of the biomass added to test samples was attached to the sedimen
机译:确定了菲和荧蒽的生物降解动力学,作为其溶解浓度的函数,用于海洋多环芳烃降解富集。然后测定存在人工吸附(腐殖酸涂层的硅藻土)或带有吸附的PAH的Puget Sound沉积物时的生物降解速率。预期这些速率比没有沉淀物的测试要慢,这是由于在可溶性相中PAH受限制,这是由于PAH从固相到液相的解吸限制。由于PAH化合物的含水PAH浓度低,在批次降解测试中,使用放射性标记的PAH化合物跟踪PAH化合物的命运。放射性标记的化合物以释放出的CO2,未反应的PAH处于溶解相或吸附至沉积物的形式以及非极性中间产物的形式出现。落射荧光显微镜用于确定在PAH降解过程中,富含锰的细菌是否可以附着在沉积物上。在没有沉积物的情况下,相对于PAH浓度,菲的一阶降解速率系数范围为0.033至0.139 L / mg-d,这取决于测试海洋富集的时间。无沉积物的荧蒽一级降解速率系数为0.132和0.162 L / mg-d。在存在沉积物的情况下,菲和荧蒽的降解速度分别是相同的多环芳烃和没有沉淀的生物量浓度下降解速度的2.1至3.5倍和2.1至5.3倍。在菲存在的情况下,将约50%的添加到测试样品中的生物量附着到沉积物上

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