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Optimisation research of petroleum hydrocarbon biodegradation in weathered drilling wastes from waste pits

机译:矿坑风化钻井废渣中石油烃生物降解的优化研究

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The aim of this article is to discuss the problem of drilling waste remediation. Analyses and research showed that material stored in waste pits could be classified as soil with a high level of petroleum impurities (total petroleum hydrocarbons [TPH] = 102,417-132,472 mg kg~(-1) dry mass). While preparing the complex technology of soil decontamination (which included primary reclamation, basic bioremediation and inoculation with biopreparations based on indigenous bacteria and fungi), laboratory tests indicated the use of an ex-situ method was fundamental. Remediation was controlled with a chromatographic method of qualitative and quantitative determination of petroleum hydrocarbons. Based on analytical data, there was the possibility to determine the effectiveness of consecutive purifying phases. Laboratory tests, following 135 days of basic bioremediation stimulated by optimum conditions to activate the growth of indigenous micro-organisms, resulted in a decrease in the TPH content, which was in the range of 52.3-72.5%. The next phase of soil decontamination lasted 135 days and involved the use of inoculation with biopreparations based on indigenous micro-organisms and fungi. This process enabled a TPH decrease of 93.8-94.3%. Laboratory biodegradation research was done with the use of the biomarker C_(30)-17α(H)21β(H)-hopane to normalize analyte (TPH, ∑_n-C_8-n-C_(22) and ∑_n-C_(23)-n-C_(36) concentrations. The calculated first-order biodegradation constants enable estimation of the purification stage dynamics and the effectiveness of the applied biopreparations. Furthermore, they represent the biodegradation degree of individual n-alkanes in subsequent stages of the soil purification process.
机译:本文的目的是讨论钻井废料修复问题。分析和研究表明,废料坑中存储的物质可归为具有高石油杂质水平的土壤(总石油烃[TPH] = 102,417-132,472 mg kg〜(-1)干质量)。在准备复杂的土壤净化技术(包括初次开垦,基本的生物修复以及基于本地细菌和真菌的生物制剂的接种)时,实验室测试表明,使用异位方法是基本的。用定性和定量测定石油烃的色谱方法控制修复。根据分析数据,有可能确定连续纯化阶段的有效性。在最佳条件下刺激135天的基本生物修复以激活本地微生物的生长后,实验室测试导致TPH含量降低,降低幅度为52.3-72.5%。下一阶段的土壤去污持续了135天,涉及使用基于本地微生物和真菌的生物制剂进行接种。此过程使TPH降低了93.8-94.3%。实验室生物降解研究使用生物标记C_(30)-17α(H)21β(H)-hopane进行归一化分析物(TPH,∑_n-C_8-n-C_(22)和∑_n-C_(23 )-n-C_(36)浓度,计算出的一阶生物降解常数可以估算纯化阶段的动力学和所用生物制剂的有效性,而且它们代表土壤后续阶段中各个正构烷烃的生物降解程度。纯化过程。

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