Scheutz Charlotte, Kjeldsen Peter
Environment & Resources, Bygningstorvet-Building 115, Technical University of Denmark, DK-2800 Lyngby, Denmark.
J Environ Qual. 2004 Jan-Feb;33(1):72-9. doi: 10.2134/jeq2004.7200.
The influence of different environmental factors on methane oxidation and degradation of hydrochlorofluorocarbons (HCFCs) was investigated in microcosms containing soil sampled at Skellingsted Landfill, Denmark. The soil showed a high capacity for methane oxidation resulting in a maximum oxidation rate of 104 microg CH4 g(-1) h(-1) and a low affinity of methane with a half-saturation constant of 2.0% v/v. The hydrochlorofluorocarbons HCFC-21 (dichlorofluoromethane) and HCFC-22 (chlorodifluoromethane) were rapidly oxidized and the oxidation occurred in parallel with the oxidation of methane. The maximal HCFC oxidation rates were 0.95 and 0.68 microg g(-1) h(-1) for HCFC-21 and HCFC-22, respectively. Increasing concentrations of HCFCs resulted in decreased methane oxidation rates. However, compared with typical concentrations in landfill gas, relatively high HCFC concentrations were needed to obtain a significant inhibition of methane oxidation. In general, the environmental factors studied influenced the degradation of HCFCs in almost the same way as they influenced methane oxidation. Temperature had a strong influence on the methanotrophic activity giving high Q10 values of 3.4 to 4.1 over the temperature range of 2 to 25 degrees C. Temperature optimum was around 30 degrees C; however, oxidation occurred at temperatures as low as 2 degrees C. A moisture content of 25% w/w yielded the maximum oxidation rate as it allowed good gas transport together with sufficient microbial activity. The optimum pH was around neutrality (pH = 6.5-7.5) showing that the methanotrophs were optimally adapted to the in situ pH, which was 6.9. Copper showed no inhibitory effect when added in relatively high concentrations (up to 60 mg kg(-1)), most likely due to sorption of copper ions to soil particles. At higher copper concentrations the oxidation rates decreased. The oxidation rates for methane, HCFC-21, and HCFC-22 were unaltered in ammonium-amended soil up to 14 mg kg(-1). Higher ammonium concentrations inhibited the oxidation process. The most important parameters controlling oxidation in landfill cover soil were found to be temperature, soil moisture, and methane and oxygen supply.
在含有从丹麦斯克林斯泰德垃圾填埋场采集的土壤的微观世界中,研究了不同环境因素对甲烷氧化和氢氯氟烃(HCFCs)降解的影响。该土壤显示出较高的甲烷氧化能力,最大氧化速率为104微克CH4克⁻¹小时⁻¹,且甲烷亲和力较低,半饱和常数为2.0%(体积/体积)。氢氯氟烃HCFC - 21(二氯氟甲烷)和HCFC - 22(氯二氟甲烷)被快速氧化,且氧化过程与甲烷氧化同时发生。HCFC - 21和HCFC - 22的最大HCFC氧化速率分别为0.95和0.68微克克⁻¹小时⁻¹。HCFCs浓度增加导致甲烷氧化速率降低。然而,与垃圾填埋气中的典型浓度相比,需要相对较高的HCFC浓度才能显著抑制甲烷氧化。总体而言,所研究的环境因素对HCFCs降解的影响方式与对甲烷氧化的影响方式几乎相同。温度对甲烷营养活性有强烈影响,在2至25℃的温度范围内,Q10值高达3.4至4.1。最适温度约为30℃;然而,在低至2℃的温度下也会发生氧化。25%(重量/重量)的含水量产生最大氧化速率,因为它既能保证良好的气体传输,又能维持足够的微生物活性。最适pH约为中性(pH = 6.5 - 7.5),这表明甲烷氧化菌最适应原位pH值,即6.9。当以相对较高的浓度(高达60毫克/千克)添加铜时,未显示出抑制作用,这很可能是由于铜离子吸附到土壤颗粒上。在较高的铜浓度下,氧化速率降低。在铵含量高达14毫克/千克的土壤中,甲烷、HCFC - 21和HCFC - 22的氧化速率未发生改变。较高的铵浓度会抑制氧化过程。发现控制垃圾填埋覆盖土壤中氧化的最重要参数是温度、土壤湿度以及甲烷和氧气供应。