Wu Q, Bedard D L, Wiegel J
Department of Microbiology, University of Georgia, Athens 30602, USA.
Appl Environ Microbiol. 1997 Dec;63(12):4818-25. doi: 10.1128/aem.63.12.4818-4825.1997.
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.
在伍兹池塘(马萨诸塞州莱诺克斯)沉积物样本中,对Aroclor 1260残留物的还原脱氯进行了为期一年的研究,孵化温度范围为4至66摄氏度。沉积物浆液在有无2,3,4,6 - 四氯联苯(2346 - CB;350微摩尔)作为Aroclor 1260残留物脱氯引发剂的情况下进行厌氧孵化。Aroclor残留物的脱氯仅发生在用2346 - CB引发的活性样本中,且仅在8至34摄氏度和50至60摄氏度时发生。多氯联苯(PCB)脱氯的程度和模式取决于温度。在8至34摄氏度时,脱氯导致六至九氯联苯减少28%至65%,三氯和四氯联苯相应增加。在12至30摄氏度时,仅3个月内,六至九氯联苯的30%至40%就被脱氯。总体氯去除的最佳温度为20至27摄氏度。我们观察到四种不同的微生物脱氯过程,其温度范围不同但部分重叠,即8至30摄氏度的过程N(间位两侧脱氯)、12至34摄氏度的过程P(对位两侧脱氯)、18至30摄氏度的过程LP(无侧翼对位脱氯)以及50至60摄氏度的过程T(特定七氯和八氯联苯的非常有限的间位脱氯)。这些温度范围应有助于制定策略,以富集和分离负责每种脱氯过程的微生物。孵化温度决定了四种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地PCB脱氯的影响应有助于预测多氯联苯在环境中的归宿或规划这些场地的生物修复策略。