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土壤中本地微生物群落对三氯乙烯和甲苯的生物降解作用。

Biodegradation of trichloroethylene and toluene by indigenous microbial populations in soil.

作者信息

Fan S, Scow K M

机构信息

Department of Land, Air and Water Resources, University of California, Davis 95616.

出版信息

Appl Environ Microbiol. 1993 Jun;59(6):1911-8. doi: 10.1128/aem.59.6.1911-1918.1993.

Abstract

The biodegradation of trichloroethylene (TCE) and toluene, incubated separately and in combination, by indigenous microbial populations was measured in three unsaturated soils incubated under aerobic conditions. Sorption and desorption of TCE (0.1 to 10 micrograms ml-1) and toluene (1.0 to 20 micrograms ml-1) were measured in two soils and followed a reversible linear isotherm. At a concentration of 1 micrograms ml-1, TCE was not degraded in the absence of toluene in any of the soils. In combination, both 1 microgram of TCE ml-1 and 20 micrograms of toluene ml-1 were degraded simultaneously after a lag period of approximately 60 to 80 h, and the period of degradation lasted from 70 to 90 h. Usually 60 to 75% of the initial 1 microgram of TCE ml-1 was degraded, whereas 100% of the toluene disappeared. A second addition of 20 micrograms of toluene ml-1 to a flask with residual TCE resulted in another 10 to 20% removal of the chemical. Initial rates of degradation of toluene and TCE were similar at 32, 25, and 18 degrees C; however, the lag period increased with decreasing temperature. There was little difference in degradation of toluene and TCE at soil moisture contents of 16, 25, and 30%, whereas there was no detectable degradation at 5 and 2.5% moisture. The addition of phenol, but not benzoate, stimulated the degradation of TCE in Rindge and Yolo silt loam soils, methanol and ethylene slightly stimulated TCE degradation in Rindge soil, glucose had no effect in either soil, and dissolved organic carbon extracted from soil strongly sorbed TCE but did not affect its rate of biodegradation.

摘要

在有氧条件下培养的三种非饱和土壤中,测定了本地微生物群落对三氯乙烯(TCE)和甲苯单独及混合培养时的生物降解情况。在两种土壤中测定了TCE(0.1至10微克/毫升)和甲苯(1.0至20微克/毫升)的吸附和解吸情况,其遵循可逆线性等温线。在浓度为1微克/毫升时,在任何一种土壤中,若没有甲苯,TCE都不会降解。混合培养时,1微克/毫升的TCE和20微克/毫升的甲苯在大约60至80小时的滞后期后同时降解,降解期持续70至90小时。通常,初始1微克/毫升的TCE中有60%至75%会被降解,而100%的甲苯会消失。向含有残留TCE的烧瓶中再次添加20微克/毫升的甲苯,会使该化学物质再去除10%至20%。在32℃、25℃和18℃时,甲苯和TCE的初始降解速率相似;然而,滞后期随温度降低而增加。在土壤湿度为16%、25%和30%时,甲苯和TCE的降解差异不大,而在湿度为5%和2.5%时未检测到降解。添加苯酚(而非苯甲酸盐)会刺激林奇和约洛粉质壤土中TCE的降解,甲醇和乙烯会略微刺激林奇土壤中TCE的降解,葡萄糖在两种土壤中均无影响,从土壤中提取的溶解有机碳会强烈吸附TCE,但不影响其生物降解速率。

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本文引用的文献

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Trichloroethylene biodegradation by a methane-oxidizing bacterium.甲烷氧化菌对三氯乙烯的生物降解。
Appl Environ Microbiol. 1988 Apr;54(4):951-6. doi: 10.1128/aem.54.4.951-956.1988.
2
Aerobic metabolism of trichloroethylene by a bacterial isolate.一株细菌分离株对三氯乙烯的需氧代谢。
Appl Environ Microbiol. 1986 Aug;52(2):383-4. doi: 10.1128/aem.52.2.383-384.1986.

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