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Degradation rates of aged petroleum hydrocarbons are likely to be mass transfer dependent in the field

机译:在现场,老化的石油碳氢化合物的降解率可能取决于传质

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Evidence for on site biodegradation may be difficult to provide at heterogeneous sites without additional experiments in controlled laboratory conditions. In this study, microbial activities measured as CO_2 and CH_4 production were compared in situ, in intact soil cores and in bottle microcosms containing sieved soils. In addition, biodegradation rates were determined by measuring the decrease in petroleum hydrocarbon concentrations at 7℃ in aerobic and anaerobic conditions. Elevated concentrations of CO_2 and CH_4 in the soil gas phase indicated that both the aerobic and anaerobic microbial activity potentials were high at the contaminated site. Aerobic and anaerobic microbial degradation rates in laboratory experiments of petroleum hydrocarbons were highest in soils from the most contaminated point and degradation in the aerobic and anaerobic microcosms was linear throughout the incubation, indicating mass-transfer-dependent degradation. Different results for microbial activity measurements were obtained in laboratory studies depending on pretreatment and size of the sample, even when the environmental conditions were mimicked. These differences may be related to differences in the gas exchange rates as well as in changes in the bioavailability of the contaminant in different analyses. When predicting by modeling the behavior of an aged contaminant it is relevant to adapt the models in use to correspond to conditions relevant at the contaminated sites. The variables used in the models should be based on data from the site and on experiments performed using the original aged contaminant without any additions.
机译:如果不在受控的实验室条件下进行额外的实验,可能很难在异质站点上提供现场生物降解的证据。在这项研究中,在原位,完整的土壤核心和含有筛分土壤的瓶装微观世界中比较了以CO_2和CH_4产生量衡量的微生物活性。此外,通过测量好氧和厌氧条件下7℃下石油烃浓度的降低来确定生物降解率。土壤气相中CO_2和CH_4的浓度升高表明,受污染场地的需氧和厌氧微生物活性潜力都很高。从污染程度最高的土壤来看,石油烃实验室实验中好氧和厌氧微生物的降解率最高,并且在整个培养过程中,好氧和厌氧微生物的降解是线性的,这表明依赖于传质的降解。即使在模拟环境条件的情况下,根据预处理和样品的大小,在实验室研究中也可获得不同的微生物活性测量结果。这些差异可能与气体交换速率的差异以及污染物在不同分析中的生物利用度的变化有关。当通过对老化的污染物的行为进行建模进行预测时,必须使使用的模型适应于受污染地点的相关条件。模型中使用的变量应基于现场数据和使用原始老化污染物进行的实验而无需添加任何内容。

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