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Biodegradation of dichloromethane and its utilization as a growth substrate under methanogenic conditions.

机译:甲烷的生物降解作用及其在产甲烷条件下作为生长底物的用途。

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摘要

Biodegradation of dichloromethane (DCM) to environmentally acceptable products was demonstrated under methanogenic conditions (35 degrees C). When DCM was supplied to enrichment cultures as the sole organic compound at a low enough concentration to avoid inhibition of methanogenesis, the molar ratio of CH4 formed to DCM consumed (0.473) was very close to the amount predicted by stoichiometric conservation of electrons. DCM degradation was also demonstrated when methanogenesis was partially inhibited (with 0.5 to 1.5 mM 2-bromoethanesulfonate or approximately 2 mM DCM) or completely stopped (with 50 to 55.5 mM 2-bromoethanesulfonate). Addition of a eubacterial inhibitor (vancomycin, 100 mg/liter) greatly reduced the rate of DCM degradation. 14CO2 was the principal product of [14C]DCM degradation, followed by 14CH4 (when methanogenesis was uninhibited) or 14CH3COOH (when methanogenesis was partially or completely inhibited). Hydrogen accumulated during DCM degradation and then returned to background levels when DCM was consumed. These results suggested that nonmethanogenic organisms mediated DCM degradation, oxidizing a portion to CO2 and fermenting the remainder to acetate; acetate formation suggested involvement of an acetogen. Methanogens in the enrichment culture then converted the products of DCM degradation to CH4. Aceticlastic methanogens were more easily inhibited by 2-bromoethanesulfonate and DCM than were CO2-reducing methanogens. When DCM was the sole organic-carbon and electron donor source supplied, its use as a growth substrate was demonstrated. The highest observed yield was 0.085 g of suspended organic carbon formed per g of DCM carbon consumed. Approximately 85% of the biomass formed was attributable to the growth of nonmethanogens, and 15% was attributable to methanogens.
机译:在产甲烷条件下(35摄氏度)证明了二氯甲烷(DCM)生物降解为环境可接受的产品。当以足够低的浓度将DCM作为唯一的有机化合物提供给富集培养物时,避免抑制甲烷生成,所形成的CH4与消耗的DCM的摩尔比(0.473)非常接近电子化学计量守恒的预测量。当甲烷生成被部分抑制(用0.5至1.5 mM的2-溴乙烷磺酸盐或约2 mM DCM)或完全停止(用50至55.5 mM的2-溴乙烷磺酸盐)时,也证明了DCM降解。加入真细菌抑制剂(万古霉素,100 mg / L)可大大降低DCM的降解率。 14CO2是[14C] DCM降解的主要产物,其次是14CH4(当甲烷生成不受抑制时)或14CH3COOH(当甲烷生成被部分或完全抑制时)。在DCM降解期间积累的氢气,然后在消耗DCM时返回本底水平。这些结果表明,非甲烷源性生物体介导了DCM的降解,将一部分氧化为CO2,并将其余的发酵为乙酸。乙酸盐的形成表明有乙酸原的参与。然后,富集培养物中的产甲烷菌将DCM降解产物转化为CH4。与减少CO 2的产甲烷菌相比,2-溴乙烷磺酸盐和DCM更容易抑制乙腈的产甲烷菌。当DCM是唯一提供的有机碳和电子供体来源时,证明了DCM作为生长基质的用途。观察到的最高产量是每消耗1克DCM碳形成0.085克悬浮有机碳。形成的生物质中约有85%归因于非甲烷原菌的生长,而15%归因于产甲烷菌。

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