Harkness M R, McDermott J B, Abramowicz D A, Salvo J J, Flanagan W P, Stephens M L, Mondello F J, May R J, Lobos J H, Carroll K M
GE Corporate Research and Development Center, Schenectady, NY 12301.
Science. 1993 Jan 22;259(5094):503-7. doi: 10.1126/science.8424172.
A 73-day field study of in situ aerobic biodegradation of polychlorinated biphenyls (PCBs) in the Hudson River shows that indigenous aerobic microorganisms can degrade the lightly chlorinated PCBs present in these sediments. Addition of inorganic nutrients, biphenyl, and oxygen enhanced PCB biodegradation, as indicated both by a 37 to 55 percent loss of PCBs and by the production of chlorobenzoates, intermediates in the PCB biodegradation pathway. Repeated inoculation with a purified PCB-degrading bacterium failed to improve biodegradative activity. Biodegradation was also observed under mixed but unamended conditions, which suggests that this process may occur commonly in river sediments, with implications for PCB fate models and risk assessments.
一项对哈得逊河中多氯联苯(PCBs)进行73天原位好氧生物降解的实地研究表明,本地好氧微生物能够降解这些沉积物中存在的轻度氯化多氯联苯。添加无机养分、联苯和氧气可增强多氯联苯的生物降解,这在多氯联苯损失37%至55%以及多氯联苯生物降解途径中的中间体氯苯甲酸酯的产生中都得到了体现。用纯化的多氯联苯降解细菌反复接种未能提高生物降解活性。在混合但未添加物质的条件下也观察到了生物降解,这表明该过程可能在河流沉积物中普遍发生,对多氯联苯归宿模型和风险评估具有重要意义。