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控制硝酸盐和硫酸盐的释放以增强海洋沉积物中菲的厌氧生物修复。

Controlled release of nitrate and sulfate to enhance anaerobic bioremediation of phenanthrene in marine sediments.

作者信息

Tang Yinjie J, Carpenter Shelly, Deming Jody, Krieger-Brockett Barbara

机构信息

Departments of Chemical Engineering and Oceanography, University of Washington, Seattle, Washington 98195, USA.

出版信息

Environ Sci Technol. 2005 May 1;39(9):3368-73. doi: 10.1021/es040427w.

Abstract

Experimental measurements demonstrated that rates of in situ microbial anaerobic biodegradation of phenanthrene in undisturbed marine sediments were enhanced when controlled-release electron acceptors (i.e., nitrate and sulfate (for comparison)) were employed. The experimental method used whole and interval cores injected with radiolabeled 14C-phenanthrene, which were incubated, sacrificed, and processed for 14CO2 recovery to determine degradation rates. Nitrocellulose and CaSO4 were formulated to release the electron acceptors into the sediments at rates consistent with bacterial utilization (i.e., that avoided inhibition observed previously at high soluble nitrate (although not sulfate) concentrations). The controlled-release of both compounds, measured in collateral experiments, enhanced the natural anaerobic phenanthrene biodegradation rates by factors up to 2-3. Biodegradation via sulfate reduction was most rapid in the early stages (24 days) of experiments, consistent with reports that many marine bacteria in submerged sediments are sulfate reducers. In comparison, in longer experiments (after 42 days), the anaerobic biodegradation rates were observed at least as high with the addition of nitrocellulose (over 40% of added phenanthrene recovered as 14CO2). Both nitrate and sulfate reduction was observed during anaerobic incubation, although the presence of nitrate seemed to reduce the sulfate reduction. The studied forms of the controlled-release nitrate and sulfate may provide capping amendments to decontaminate marine harbor sediments.

摘要

实验测量表明,当使用控释电子受体(即硝酸盐和硫酸盐(用于比较))时,未受干扰的海洋沉积物中菲的原位微生物厌氧生物降解速率会提高。实验方法是使用注入放射性标记的14C-菲的完整岩心和间隔岩心,对其进行培养、取样并处理以回收14CO2来确定降解速率。硝化纤维素和硫酸钙被配制为以与细菌利用速率一致的速度将电子受体释放到沉积物中(即避免了之前在高可溶性硝酸盐(尽管不是硫酸盐)浓度下观察到的抑制作用)。在并行实验中测量的这两种化合物的控释,使天然厌氧菲生物降解速率提高了2至3倍。在实验的早期阶段(24天),通过硫酸盐还原进行的生物降解最为迅速,这与许多淹没沉积物中的海洋细菌是硫酸盐还原菌的报道一致。相比之下,在更长时间的实验中(42天后),添加硝化纤维素时观察到的厌氧生物降解速率至少同样高(超过40%添加的菲以14CO2形式回收)。在厌氧培养过程中观察到了硝酸盐和硫酸盐的还原,尽管硝酸盐的存在似乎降低了硫酸盐的还原。所研究的控释硝酸盐和硫酸盐形式可能为净化海洋港口沉积物提供覆盖性改良剂。

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