Center for Marine Environmental Studies, Ehime University, Matsuyama, Ehime, Japan.
FEMS Microbiol Ecol. 2013 Jul;85(1):168-78. doi: 10.1111/1574-6941.12108. Epub 2013 Apr 5.
Soil bacterial population dynamics were examined to assess patterns in microbial response to contamination by different petroleum mixtures with variation in n-alkane profiles or toxic constituents such as pentachlorophenol (PCP). Three soil types from distinct areas of the United States (Montana, Oregon, and Arizona) were used in controlled perturbation experiments containing crude oil, kerosene, diesel, or diesel plus PCP spiked with (14)C-hexadecane or (14)C-tridecane. After a 50-day incubation, 30-70% of added (14)C-alkanes were mineralized to (14)CO₂ in Montana and Oregon soils. In contrast, significantly lower mineralization was observed with diesel or kerosene (< 5%) compared to crude-oil treatment (~45%) in the Arizona soil. Different hydrocarbon mixtures selected both unique and common microbial populations across all three soils. Conversely, the contamination of different soils with the same mixture selected for distinct microbial populations. The most consistent genotype observed, a Rhodococcus-like population, was present in the Montana soil with all mixture types. The addition of PCP selected for PCP-tolerant alkane-degrading specialist populations. The results indicated that petroleum mixture type influenced hydrocarbon degradation rates and microbial population selection and that soil characteristics, especially organic content, could also be an important determinant of community responses to hydrocarbon perturbation.
研究了土壤细菌种群动态,以评估微生物对不同石油混合物污染的反应模式,这些混合物的正构烷烃分布或有毒成分(如五氯苯酚(PCP))存在差异。本研究使用了来自美国三个不同地区(蒙大拿州、俄勒冈州和亚利桑那州)的三种土壤进行控制扰动实验,实验中含有原油、煤油、柴油或添加了(14)C-十六烷或(14)C-十三烷的柴油加 PCP。在 50 天的孵育后,蒙大拿州和俄勒冈州土壤中添加的(14)C-烷烃中有 30-70%被矿化为(14)CO₂。相比之下,在亚利桑那州土壤中,与原油处理相比(~45%),柴油或煤油的矿化率明显较低(<5%)。不同的碳氢化合物混合物在所有三种土壤中选择了独特和共同的微生物种群。相反,不同土壤受到相同混合物的污染选择了不同的微生物种群。观察到的最一致的基因型是类似于 Rhodococcus 的种群,存在于蒙大拿州的所有混合物类型中。PCP 的添加选择了耐受 PCP 的烷烃降解专家种群。结果表明,石油混合物类型影响碳氢化合物降解速率和微生物种群选择,土壤特性,特别是有机含量,也可能是群落对碳氢化合物扰动反应的重要决定因素。