首页> 美国卫生研究院文献>Applied and Environmental Microbiology >Temperature determines the pattern of anaerobic microbial dechlorination of Aroclor 1260 primed by 2346-tetrachlorobiphenyl in Woods Pond sediment.
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Temperature determines the pattern of anaerobic microbial dechlorination of Aroclor 1260 primed by 2346-tetrachlorobiphenyl in Woods Pond sediment.

机译:温度决定了伍兹池塘沉积物中2346-四氯联苯引发的Aroclor 1260厌氧微生物脱氯模式。

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摘要

Reductive dechlorination of the Aroclor 1260 residue in Woods Pond (Lenox, Mass.) sediment samples was investigated for a year at incubation temperatures from 4 to 66 degrees C. Sediment slurries were incubated anaerobically with and without 2,3,4,6-tetrachlorobiphenyl (2346-CB; 350 microM) as a primer for dechlorination of the Aroclor 1260 residue. Dechlorination of the Aroclor residue occurred only in live samples primed with 2346-CB and only at 8 to 34 degrees C and 50 to 60 degrees C. The extent and pattern of polychlorinated biphenyl (PCB) dechlorination were temperature dependent. At 8 to 34 degrees C, the dechlorination resulted in 28 to 65% decreases of the hexathrough nonachlorobiphenyls and corresponding increases in the tri- and tetrachlorobiphenyls. At 12 to 30 degrees C, 30 to 40% of the hexa- through nonachlorobiphenyls were dechlorinated in just 3 months. The optimal temperature for overall chlorine removal was 20 to 27 degrees C. We observed four different microbial dechlorination processes with different but partially overlapping temperature ranges, i.e., Process N (flanked meta dechlorination) at 8 to 30 degrees C, Process P (flanked para dechlorination) at 12 to 34 degrees C, Process LP (unflanked para dechlorination) at 18 to 30 degrees C, and Process T (a very restricted meta dechlorination of specific hepta- and octachlorobiphenyls) at 50 to 60 degrees C. These temperature ranges should aid in the development of strategies for the enrichment and isolation of the microorganisms responsible for each dechlorination process. The incubation temperature determined the relative dominance of the four PCB dechlorination processes and the extent and products of dechlorination. Hence, understanding the effects of temperature on PCB dechlorination at contaminated sites should assist in predicting the environmental fate of PCBs or planning bioremediation strategies at those sites.
机译:在4至66摄氏度的培养温度下研究了伍兹池塘(马萨诸塞州莱诺克斯)沉积物样品中Aroclor 1260残留物的还原脱氯一年。 (2346-CB; 350 microM)作为Aroclor 1260残留物脱氯的引物。 Aroclor残留物的脱氯仅在用2346-CB灌注的活样品中发生,并且仅在8至34摄氏度和50至60摄氏度下发生。多氯联苯(PCB)脱氯的程度和方式与温度有关。在8至34摄氏度下,脱氯导致六通九氯联苯减少28%至65%,三氯联苯和四氯联苯相应增加。在12至30摄氏度下,仅3个月即可将30%至40%的六氯至九氯联苯脱氯。整体除氯的最佳温度为20到27摄氏度。我们观察到四个不同的微生物脱氯过程,它们具有不同但部分重叠的温度范围,即在8到30摄氏度之间的过程N(侧向间脱氯),过程P(对位侧)在12至34摄氏度下进行脱氯,在18至30摄氏度下进行工艺LP(无侧链对氯脱氯)和在50至60摄氏度下进行工艺T(对特定的七氯和八氯联苯进行非常严格的间位脱氯)。这些温度范围应协助制定策略来丰富和分离负责每个脱氯过程的微生物。孵育温度决定了四个PCB脱氯过程的相对优势以及脱氯的程度和产物。因此,了解温度对受污染场所PCB脱氯的影响应有助于预测PCB的环境命运或规划这些场所的生物修复策略。

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