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The Effects of Nitrogen Source and Supply on Bioventing of Gasoline Contaminated Soil

机译:氮源和供应对汽油污染土壤生物排放的影响

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Soil remediation through bioventing is becoming a popular in situ technology for treatment of hydrocarbon contaminated soil. Bioventing removes residual contamination left by soil vapour extraction (SVE) using low or intermittent airflow rates to produce oxygen-rich conditions in the vadose zone. This promotes the growth of indigenous microorganisms which degrade the hydrocarbon contaminant, provided sufficient nutrients are available. However, there are major questions that remain to be answered, including the optimum soil moisture content, type and amount of nutrients necessary and means of producing these conditions in the field. Accordingly, respirometer experiments were conducted using gasoline contaminated soil from a site in Ontario, Canada. The experiments conducted were designed to determine the optimum C:N ratio and the optimum form or combination of nitrogen supply. The completed experiments gave an optimum biodegradation rate constant of 0.0806 d~(-1) for soil amended with ammonia at a C:N ratio of 10:1, and a moisture content of 15w/w%. Minimal acidification was observed at a C:N ratio of 10:1, indicating that it is unlikely that inhibition will occur at a ratio of 20:1. Accordingly, future experiments will investigate a higher nutrient application rate of C:N = 5:1. While the degradation results agree with literature data, the microbial enumeration tests indicate that the degradation may not necessarily be due to bacterial metabolism. Future experiments will attempt to determine the mechanism of degradation by isolating bacterial and fungal soil microorganisms and repeating the bioventing trials.
机译:通过生物排放进行的土壤修复正成为处理碳氢化合物污染土壤的流行原位技术。生物通风利用低或间断的气流速率消除了土壤蒸汽提取(SVE)留下的残留污染,从而在渗流带中产生了富氧条件。只要有足够的养分,这将促进降解碳氢化合物污染物的本地微生物的生长。但是,还有一些主要问题有待解决,包括最佳的土壤水分含量,必需的养分类型和数量以及在田间产生这些条件的方法。因此,呼吸仪实验是使用加拿大安大略省某地的汽油污染土壤进行的。设计进行的实验以确定最佳的C:N比和最佳的氮气供应形式或组合。完成的实验给出了以10:1的C:N比和15w / w%的水分比例对氨水进行改良的土壤的最佳生物降解速率常数,为0.0806 d〜(-1)。在C:N为10:1的情况下观察到最小的酸化,这表明抑制不太可能以20:1的比率发生。因此,未来的实验将研究更高的养分施用比例,C:N = 5:1。尽管降解结果与文献数据相符,但微生物计数测试表明降解可能不一定是细菌代谢所致。未来的实验将尝试通过分离细菌和真菌土壤微生物并重复进行生物排放试验来确定降解机理。

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