Oil and Gas Institute, Krosno, Poland.
Waste Manag Res. 2010 Dec;28(12):1065-75. doi: 10.1177/0734242X09351906. Epub 2009 Dec 18.
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 C30-17α(H)21β(H)-hopane to normalize analyte (TPH, Σn-C8-n-C22 and Σn-C23-n-C36) 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.
本文旨在探讨钻井废物修复问题。分析和研究表明,储存在废物坑中的物质可归类为高石油杂质含量的土壤(总石油烃[TPH]为 102,417-132,472mgkg(-1)干质量)。在准备复杂的土壤去污技术(包括初步开垦、基本生物修复和接种基于土著细菌和真菌的生物制剂)时,实验室测试表明原位方法是基础。采用色谱法对石油烃进行定性和定量测定来控制修复。基于分析数据,可以确定连续净化阶段的效果。经过 135 天的基本生物修复,在最佳条件下刺激土著微生物的生长,实验室测试结果表明总石油烃含量下降了 52.3-72.5%。下一个土壤去污阶段持续了 135 天,涉及使用基于土著微生物和真菌的生物制剂接种。这一过程使总石油烃含量下降了 93.8-94.3%。使用生物标志物 C30-17α(H)21β(H)-藿烷对分析物(TPH、Σn-C8-n-C22 和 Σn-C23-n-C36)浓度进行归一化,进行了实验室生物降解研究。计算得到的一级生物降解常数可用于估计净化阶段的动态和应用生物制剂的有效性。此外,它们还代表了在土壤净化过程的后续阶段中,个别正构烷烃的生物降解程度。