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CASE HISTORY FOR TREATING CONTAMINATED GROUNDWATER WITH COMETABOLIC METHANOTROPHIC BIOREMEDIATION

机译:用Cometabolic甲脂蛋白生物修复治疗污染地下水的案例历史

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Site investigations at a manufacturing facility in Virginia identified three soil and groundwater contaminant source areas. Each source area had a different volatile organic compound (VOC) profile of chlorinated solvents trichloroethylene (TCE); 1,1,1- trichloroethane (TCA); and associated breakdown products (cis-1, 2-dichloroethene (DCE), vinyl chloride (VC), 1,1-dichloroethane (DCA), and chloroethane (CA)); as well as acetone and isopropanol in soil and groundwater in a fractured rock aquifer. Chemical and microbiological sampling over time confirmed that natural biodegradation of these compounds was occurring at a limited rate. In-situ aerobic cometabolic bioremediation was implemented at three on-site source areas to stimulate existing microbial populations to accelerate the degradation of target VOCs. Results of pilot and full-scale bioremediation efforts have been successful to varying degrees at each of these different locations. The first source area at this site where the bioremediation technology was applied contained the chlorinated hydrocarbons, acetone and isopropanol. Monitoring data indicate that the enhanced bioremediation program has been successful in stimulating microbial growth based on increases in phospholipid fatty acid (PLFA) biomass and methanotroph most probable number (MPN) measurements of several orders of magnitude within four months of system start-up throughout full-scale operation. Initial total VOC concentrations ranged from 10,000 ug/l to >1,000,000 ug/l. Groundwater monitoring indicates significant (99 to 99.96%) total VOC reductions in this source area, and in some downgradient monitoring locations. However, after this significant VOC reduction, VOC concentrations in groundwater from some of the monitoring wells remain above drinking water standards despite approximately four years of system operation. The second source area contained primarily acetone and isopropanol in groundwater. The acetone and isopropanol concentrations in this source area ranged from 200,000 ug/l to 500,000 ug/l for each compound prior to initiation of the bioremediation system. Following three months of system operation, the acetone and isopropanol concentrations were below detection limits in several wells.
机译:在弗吉尼亚州制造业设施的现场调查确定了三种土壤和地下水污染源区域。每个源区具有不同的挥发性有机化合物(VOC)氯乙烯(TCE); 1,1,1-三氯乙烷(TCA);和相关的分解产物(CIS-1,2-二氯乙烯(DCE),氯乙烯(VC),1,1-二氯乙烷(DCA)和氯乙烷(CA));以及碎裂的岩石含水层的土壤和地下水中的丙酮和异丙醇。随着时间的推移,化学和微生物取样证实,这些化合物的天然生物降解以有限的速率发生。原位有氧Cometabolic生物修复在三个现场源区实施,以刺激现有的微生物群,以加速目标VOC的降解。飞行员和全规模生物修复的结果已经成功地在这些不同地点的每个地方变为不同程度。应用生物修复技术的第一个源区含有氯化烃,丙酮和异丙醇。监测数据表明,增强的生物修复程序在磷脂脂肪酸(PLFA)生物质和甲蛋白最大可能的数量(MPN)的增加的情况下,在系统启动的四个月内的几个数量级的增加,基于磷脂脂肪酸(PLFA)生物量和甲蛋白最大可能的数量(MPN)测量的增加,这是成功的-scale操作。初始总VOC浓度范围从10,000 UG / L到> 1,000,000 UG / L.地下水监测表明该源区的总体VOC减少了显着(99%至99.96%,以及一些下坡监测位置。然而,在这一重要的VOC减少之后,尽管大约四年的系统运行,但在饮用水标准之后,地下水的VOC浓度仍然高于饮用水标准。第二源区主要包含丙酮和地下水中的异丙醇。在开始生物化系统之前,该源区中的丙酮和异丙醇浓度为每种化合物的200,000ug / L至500,000ug / l。在系统运行三个月后,丙酮和异丙醇浓度低于几个孔的检测限。

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