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2
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6
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Anaerobic biodegradation of 2,4,5-trichlorophenoxyacetic Acid in samples from a methanogenic aquifer: stimulation by short-chain organic acids and alcohols.产甲烷含水层中 2,4,5-三氯苯氧乙酸的厌氧生物降解:短链有机酸和醇的刺激作用。
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8
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10
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Isolation and partial characterization of bacteria in an anaerobic consortium that mineralizes 3-chlorobenzoic Acid.在一个能够使 3-氯苯甲酸矿化的厌氧生物群落中分离和部分鉴定细菌。
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Kinetics of microbial dehalogenation of haloaromatic substrates in methanogenic environments.产甲烷环境中卤代芳烃微生物脱卤动力学。
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Anaerobic biodegradation of chlorophenols in fresh and acclimated sludge.新鲜污泥和驯化污泥中氯酚的厌氧生物降解
Appl Environ Microbiol. 1984 Feb;47(2):272-7. doi: 10.1128/aem.47.2.272-277.1984.
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Anaerobic biodegradation of phenolic compounds in digested sludge.消化污泥中酚类化合物的厌氧生物降解
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不同温度下淡水湖沉积物中2,4-二氯苯酚的厌氧生物降解

Anaerobic biodegradation of 2,4-dichlorophenol in freshwater lake sediments at different temperatures.

作者信息

Kohring G W, Rogers J E, Wiegel J

机构信息

Center for Biological Resource Recovery, University of Georgia, Athens 30602.

出版信息

Appl Environ Microbiol. 1989 Feb;55(2):348-53. doi: 10.1128/aem.55.2.348-353.1989.

DOI:10.1128/aem.55.2.348-353.1989
PMID:2719477
原文链接:https://pmc.ncbi.nlm.nih.gov/articles/PMC184113/
Abstract

Anaerobic degradation of 2,4-dichlorophenol (2,4-DCP) between 5 and 72 degrees C was investigated. Anaerobic sediment slurries prepared from local freshwater pond sediments were partitioned into anaerobic tubes or serum vials, which then were incubated separately at the various temperatures. Reductive 2,4-DCP dechlorination occurred only in the temperature range between 5 and 50 degrees C, although methane was formed up to 60 degrees C. In sediment samples from two sites and at all tested temperatures from 5 to 50 degrees C, 2,4-DCP was transformed to 4-chlorophenol (4-CP). The 4-CP intermediate was subsequently degraded after an extended lag period in the temperature range from 15 to 40 degrees C. Adaptation periods for 2,4-DCP transformation decreased between 5 and 25 degrees C, were essentially constant between 25 and 35 degrees C, and increased in the tubes incubated at temperatures between 35 and 40 degrees C. The degradation rates increased exponentially between 15 and 30 degrees C, had a second peak at 35 degrees C, and decreased to about 5% of the peak activity by 40 degrees C. In tubes from one sediment sample, incubated at temperatures above 40 degrees C, an increase in the degradation rate was observed following the minimum at 40 degrees C. This suggests that at least two different organisms were involved in the transformation of 2,4-DCP to 4-CP. Storage of the original sediment slurries for 2 months at 12 degrees C resulted in increased adaptation times, but did not affect the degradation rates.

摘要

研究了5至72摄氏度之间2,4 - 二氯苯酚(2,4 - DCP)的厌氧降解情况。用当地淡水池塘沉积物制备的厌氧沉积物浆液被分装到厌氧管或血清瓶中,然后分别在不同温度下孵育。尽管在高达60摄氏度时会生成甲烷,但2,4 - DCP的还原脱氯仅发生在5至50摄氏度的温度范围内。在来自两个地点的沉积物样本以及5至50摄氏度的所有测试温度下,2,4 - DCP都转化为了4 - 氯苯酚(4 - CP)。在15至40摄氏度的温度范围内,经过一段延长的滞后期后,4 - CP中间体随后被降解。2,4 - DCP转化的适应期在5至25摄氏度之间缩短,在25至35摄氏度之间基本恒定,而在35至40摄氏度孵育的管中则延长。降解速率在15至30摄氏度之间呈指数增加,在35摄氏度时有第二个峰值,到40摄氏度时降至峰值活性的约5%。在一个沉积物样本的管中,在高于40摄氏度的温度下孵育,在40摄氏度达到最小值后观察到降解速率增加。这表明至少有两种不同的生物体参与了2,4 - DCP向4 - CP的转化。将原始沉积物浆液在12摄氏度下储存2个月导致适应时间增加,但不影响降解速率。