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土壤中芘、苯并[a]芘和咔唑的原生和强化矿化作用

Indigenous and enhanced mineralization of pyrene, benzo[a]pyrene, and carbazole in soils.

作者信息

Grosser R J, Warshawsky D, Vestal J R

机构信息

Department of Biological Sciences, University of Cincinnati, Ohio 45221.

出版信息

Appl Environ Microbiol. 1991 Dec;57(12):3462-9. doi: 10.1128/aem.57.12.3462-3469.1991.

Abstract

We studied the mineralization of pyrene, carbazole, and benzo[a]pyrene in soils obtained from three abandoned coal gasification plants in southern Illinois. The soils had different histories of past exposure to hydrocarbon contamination and different amounts of total organic carbon, microbial biomass, and microbial activity. Mineralization was measured by using serum bottle radiorespirometry. The levels of indigenous mineralization of 14C-labeled compounds ranged from 10 to 48% for pyrene, from undetectable to 46% for carbazole, and from undetectable to 25% for benzo[a]pyrene following long-term (greater than 180-day) incubations. Pyrene and carbazole were degraded with short or no lag periods in all soils, but benzo[a]pyrene mineralization occurred after a 28-day lag period. Mineralization was not dependent on high levels of microbial biomass and activity in the soils. Bacterial cultures that were capable of degrading pyrene and carbazole were isolated by enrichment, grown in pure culture, and reintroduced into soils. Reintroduction of a pyrene-degrading bacterium enhanced mineralization to a level of 55% within 2 days, compared with a level of 1% for the indigenous population. The carbazole degrader enhanced mineralization to a level of 45% after 7 days in a soil that showed little indigenous carbazole mineralization. The pyrene and carbazole degraders which we isolated were identified as a Mycobacterium sp. and a Xanthamonas sp., respectively. Our results indicated that mineralization of aromatic hydrocarbons can be significantly enhanced by reintroducing isolated polycyclic aromatic hydrocarbon-degrading bacteria.

摘要

我们研究了从伊利诺伊州南部三个废弃煤气化厂采集的土壤中芘、咔唑和苯并[a]芘的矿化情况。这些土壤过去接触碳氢化合物污染的历史不同,总有机碳、微生物生物量和微生物活性的含量也不同。矿化作用通过血清瓶放射性呼吸测定法进行测量。经过长期(超过180天)培养后,14C标记化合物的原生矿化水平芘为10%至48%,咔唑为未检测到至46%,苯并[a]芘为未检测到至25%。在所有土壤中,芘和咔唑在短时间或无延迟期的情况下被降解,但苯并[a]芘的矿化在28天的延迟期后发生。矿化作用并不依赖于土壤中高水平的微生物生物量和活性。通过富集培养分离出能够降解芘和咔唑的细菌培养物,在纯培养中生长,然后重新引入土壤。重新引入一种芘降解细菌后,在2天内矿化作用增强到55%的水平,而原生菌群的矿化水平为1%。在一种原生咔唑矿化很少的土壤中,咔唑降解菌在7天后将矿化作用增强到45%的水平。我们分离出的芘和咔唑降解菌分别被鉴定为一种分枝杆菌属细菌和一种黄单胞菌属细菌。我们的结果表明,通过重新引入分离出的多环芳烃降解细菌,可以显著增强芳烃的矿化作用。

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