阴离子表面活性剂在石油污染土壤生物修复中的生物降解研究

A. Selberg, J. Budashova, K. Uiga, T. Tenno
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引用次数: 0

摘要

表面活性剂在污染土壤的处理中被用作乳化剂或增溶剂。疏水性有机化合物污染土壤的表面活性剂增强修复引起了二次污染问题。一些研究表明,表面活性剂在有氧条件下是可生物降解的,其可生物降解性取决于表面活性剂的化学性质和浓度。研究土壤中表面活性剂的浸出是很重要的,因为很难确定土壤中污染物浓度降低的原因:是降解还是浸出?以细砂土为实验对象,采用柱形试验,添加CaCO3提高土壤ph,并用生物修复剂SR-100对土壤进行两次处理。测定了不同深度土壤ph、阴离子表面活性剂和石油烃的浓度。用呼吸计测定土壤各组分的微生物活性。表面活性剂以亚甲基蓝活性物质(MBAS)比色法测定其浓度。阴离子表面活性剂的浓度在柱的上层降低,而在柱的下层升高。表明在60天的试验中阴离子表面活性剂从土壤中浸出的情况。污染土壤样品中表面活性剂残留量低于未污染土壤样品。土壤低组分样品的微生物活性高于高组分样品。由于土壤过于干燥,土壤pH以pHH20、pHKcl和pHcac12代替土壤溶液pH测量。细砂土的pH值为5.8,试验期间下层土壤pH值逐渐升高,直至pHH20 = 7.5。
本文章由计算机程序翻译,如有差异,请以英文原文为准。
Biodegradation of anionic surfactants in the bioremediation of oil-polluted soil
Surfactants are applied as emulsifiers or solubilizers by treatment of polluted soil. Theproblem of secondary pollution has arisen as result of the surfactant-enhanced remediation ofa polluted soil contaminated with hydrophobic organic compounds. Several studies haveshown that the surfactants are biodegradable in aerobic conditions and the biodegradabilitydepended on the chemical properties and concentration of surfactant. A study of the leachingof surfactants from the soil is important, as it is difficult to identify the reason for thereduction of concentration of pollutants in the soil: is it degradation or leaching? Theexperiments were carried out with a fine sandy soil in column tests and CaCO3 was added toincrease soil pH. The soil was treated twice with the bioremediation agent SR-100. The soilpH, the concentrations of anionic surfactant and petroleum hydrocarbons at the differentdepths of soil were determined. The microbial activity of soil fractions was evaluated byrespirometer. The concentration of surfactants was determined colorimetrically as MethyleneBlue active substances (MBAS). The concentration of anionic surfactants decreased in theupper layer of the columns, but it increased in the lower layers. It indicated the leaching ofthe anionic surfactants from soil during experiments of 60 days. The amounts of residualsurfactants were lower in the samples of polluted soil in comparison with unpolluted soil. Thesamples of lower soil fractions had higher microbial activity in comparison with upperfractions. Soil pH was measured as pHH20, pHKcl and pHcac12 instead of the pH of soilsolution, because soil was too dry. The pH of fine sandy soil was 5.8 and during theexperiment the value of pH increased in the lower layer of soil till pHH20 = 7.5.
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