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首页> 外文期刊>Microbial Ecology >Geochemical and Physiological Evidence for Mixed Aerobic and Anaerobic Field Biodegradation of Coal Tar Waste by Subsurface Microbial Communities
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Geochemical and Physiological Evidence for Mixed Aerobic and Anaerobic Field Biodegradation of Coal Tar Waste by Subsurface Microbial Communities

机译:地下微生物群落对煤焦油废物有氧和厌氧混合生物降解的地球化学和生理证据

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We used geochemical analyses of groundwater and laboratory-incubated microcosms to investigate the physiological responses of naturally occurring microorganisms to coal-tar-waste constituents in a contaminated aquifer. Waters were sampled from wells along a natural hydrologic gradient extending from uncontaminated (1 well) into contaminated (3 wells) zones. Groundwater analyses determined the concentrations of carbon and energy sources (pollutants or total organic carbon), final electron acceptors (oxygen, nitrate, sulfate), and metabolic byproducts (dissolved inorganic carbon [DIC], alkalinity, methane, ferrous iron, sulfide, Mn2+). In the contaminated zone of the study site, concentrations of methane, hydrogen, alkalinity, and DIC were enhanced, while dissolved oxygen and nitrate were depleted. Field-initiated biodegradation assays using headspace-free serum bottle microcosms filled with groundwater examined metabolism of the ambient organic contaminants (naphthalene, 2-methylnaphthalene, benzothiophene, and indene) by the native microbial communities. Unamended microcosms from the contaminated zone demonstrated the simultaneous degradation of several coal-tar-waste constituents at the in situ temperature (10°C). Lag phases prior to the onset of biodegradation indicated the prevalence of both aerobic and anaerobic conditions in situ. Electron acceptor-amended microcosms from the most contaminated well waters demonstrated only aerobic naphthalene degradation. Collectively, the geochemical and microbial evidence show that biodegradation of coal-tar-waste constituents occurs via both aerobic and anaerobic terminal electron accepting processes at this site.
机译:我们使用了地下水的地球化学分析和实验室培养的微观世界,来研究天然微生物对受污染含水层中煤焦油废物成分的生理反应。沿自然水文梯度从井中取样水,水梯度从未污染的(1井)延伸到污染的(3井)区域。地下水分析确定了碳和能源(污染物或总有机碳),最终电子受体(氧,硝酸盐,硫酸盐)和代谢副产物(溶解的无机碳[DIC],碱度,甲烷,亚铁,硫化铁,Mn2 +)的浓度)。在研究地点的污染区,甲烷,氢气,碱度和DIC的浓度增加了,而溶解氧和硝酸盐却被消耗了。使用无顶空的血清瓶微观空间充满地下水的现场启动的生物降解测定法检查了原生微生物群落对周围有机污染物(萘,2-甲基萘,苯并噻吩和茚)的代谢。来自污染区的未经修改的微观世界表明,在原位温度(10°C)下,几种煤焦油废物成分同时降解。生物降解开始之前的滞后阶段表明原位有氧和厌氧条件的普遍性。来自受污染最严重的井水的电子受体修饰的缩影仅显示出好氧萘的降解。总的来说,地球化学和微生物证据表明,煤焦油废物成分的生物降解是通过该地点的好氧和厌氧终端电子接受过程发生的。

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