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Polycyclic aromatic hydrocarbon degradation by developed consortium in microcosms study.

机译:在微观研究中开发的财团对多环芳烃的降解。

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A feasibility study was conducted prior to onsite full-scale bioremediation study. This feasibility study has investigated the possibility of bioaugmentation of polycyclic aromatic hydrocarbon (PAH)-polluted soil with PAH-degrading strains or consortia. Five treatment options- Oil alone, Oil + Indigenous microflora, Oil + nutrients, Oil + nutrient + tilling, Oil + nutrient + tilling + developed consortium were evaluated. Out of five treatments the application of bacterial consortium, nutrients and environmental factors resulted in 79.16% removal of TPH in 60days, compared to 30.24% removal of TPH carried out by indigenous microflora. The results of High-pressure liquid chromatographic analysis showed that the ratio of di / tri aromatics decreased from initial 0.63 to 0.25 with progressive treatment of nutrient addition, nutrient+tilling, nutrient+tilling+microbial seeding. Similar effect was observed in di / di+tri aromatics ratios which also decreased 0.31 to 0.20 by bioaugmentation only. Introduction Polycyclic aromatic hydrocarbons (PAHs) constitute a group of priority environmental pollutants, which are ubiquitous contaminants in soils and sediments and are of environmental concern because of their toxic, mutagenic and/or carcinogenic effects (Mastrangelo et al., 1996 Marston et al., 2001; Xue & Warshawsky, 2005, Mallick et al ., 2007). Bioremediation is a technique that enhances the natural rate of biodegradation of pollutants through reactions carried out by selected microorganisms (Providenti et al., 1993). Bioremediation of agricultural land polluted with polycyclic aromatic hydrocarbons (PAHs), can be achieved in two ways: by enhancing the growth and activity of microorganisms already present at the site of pollution through nutrient addition (a process, called by some “biostimulation”), and by adding more selected microorganisms (Bioaugmentation) to the pollution site (Ted and Udall, 1991; Andrew and Jackson, 1996). The use of bacteria to achieve these functions has been widely studied (Atlas, 1981; Rocha et al., 1992; Kampfer et al., 1991; Mercade et al., 1996). Various studies have investigated the possibility of bioaugmentation of polycyclic aromatic hydrocarbon (PAH)-polluted soil with PAH-degrading strains or consortia.There are many definitions of 'microcosm' a typical one is that of an intact, minimally disturbed piece of an ecosystem brought into the laboratory for study in its natural state (Prichard and Bourquin, 1984). Microcosms can vary in complexity from simple static soil jars of contaminated soil to highly sophisticated systems designed to enable variations in various environmental parameters encountered on site to be more accurately simulated in the laboratory.A feasibility study was conducted to assess the short term bioremediation potential of a sandy loam soil of Haridwar region, freshly contaminated with un-weathered Sobhasan crude oil well # Y. Five treatment options- Oil alone, Oil + Indigenous Microflora, Oil + Nutrients, Oil + Nutrient (Fertilizer) + Tilling (Aeration), Oil + Nutrient (Fertilizer) + Tilling (Aeration) + Developed consortium were evaluated. An indigenous microbial consortium was developed by assembling selected microbial strains, Pseudomonas strains PS-I, PS-II and PS-III, this developed consortium was used for the cleanup of oil contaminated soil. This work reports degradation of aromatic fractions of crude oil by High pressure liquid chromatographic (HPLC) analysis to test the decontamination and conservation of a garden soil polluted with crude oil after bioremediation using “adapted” strains of Pseudomonas PS-I, PS-II and PS-III. Material And Methods Isolation and characterization of bacterial strain: The test organisms used in this study (Pseudomonas (PSI, PSII, and PSIII) were isolated from Oil production site of ONGC, oil wells from Sobhasan oil field project, Gujarat. in western India, as described elsewhere (Mittal et al., 2005). by the enrichment culture technique wi
机译:在现场全面生物修复研究之前进行了可行性研究。这项可行性研究研究了降解PAH的菌株或聚生体对多环芳烃(PAH)污染的土壤进行生物强化的可能性。评估了五个处理选项-仅油,油+本地微生物区系,油+营养素,油+营养+耕作,油+营养+耕作+发达的财团。在五种处理中,使用细菌聚生体,养分和环境因素可在60天内去除79.16%的TPH,相比之下,本地微生物群落可去除30.24%的TPH。高压液相色谱分析结果表明,随着养分的添加,养分+平铺,养分+平铺+微生物播种的逐步处理,二芳烃/三芳烃的比例从最初的0.63降低至0.25。在di / di + tri芳族化合物比率中也观察到了类似的效果,仅通过生物增强作用,该比率也降低了0.31至0.20。引言多环芳烃(PAHs)构成了一组优先的环境污染物,它们是土壤和沉积物中的普遍污染物,由于它们的有毒,致突变和/或致癌作用而受到环境关注(Mastrangelo等人,1996 Marston等人。 ,2001; Xue&Warshawsky,2005; Malrick等,2007)。生物修复是一种通过选定微生物进行的反应来提高污染物自然降解速度的技术(Providenti等,1993)。可以通过两种方式实现对被多环芳烃污染的农田的生物修复:通过添加营养物来提高污染现场已经存在的微生物的生长和活性(此过程称为“生物刺激”),通过向污染点添加更多的选定微生物(生物强化)(Ted和Udall,1991; Andrew和Jackson,1996)。已经广泛研究了使用细菌来实现这些功能(Atlas,1981; Rocha等,1992; Kampfer等,1991; Mercade等,1996)。各种各样的研究都研究了PAH降解菌株或聚生体对多环芳烃(PAH)污染的土壤进行生物强化的可能性.``微观''的定义很多,典型的定义是完整无缺的,对生态系统造成最小影响的部分。进入实验室进行自然状态的研究(Prichard和Bourquin,1984年)。从简单的受污染土壤的静态土壤罐子到旨在使现场遇到的各种环境参数的变化能够在实验室中更精确​​地模拟的高度复杂的系统,微观世界的复杂程度各不相同。进行了可行性研究,以评估植物的短期生物修复潜力。哈里瓦地区的沙质壤土,刚刚被未风化的Sobhasan原油井#Y污染。五个处理选项-单独使用油,油+本地微生物区系,油+营养素,油+营养素(肥料)+耕种(曝气),油+营养(肥料)+耕种(曝气)+开发的财团进行了评估。通过组装选定的微生物菌株,假单胞菌菌株PS-1,PS-II和PS-III,开发了一个土著微生物联合体,该联合体用于净化油污染的土壤。这项工作报告了通过高压液相色谱(HPLC)分析降解原油中的芳烃馏分,以测试使用“适应”的假单胞菌PS-I,PS-II和Pseudomonas PS-I和PS-II菌株对生物修复后被原油污染的花园土壤的去污和保存。 PS-III。材料和方法细菌菌株的分离和表征:本研究中使用的测试微生物(假单胞菌(PSI,PSII和PSIII))是从ONGC的采油场,印度古吉拉特邦Sobhasan油田项目的油井中分离出来的,如其他地方所描述的(Mittal等,2005)。

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