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Bioaugmentation and Biostimulation for Dissolved Plume Treatment at Facility 60600

机译:在设施60600的溶解羽流治疗的生物沉默和生物刺激

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Biostimulation and bioaugmentation techniques are being applied to treat a dissolved halocarbon plume at Facility 60600 on Cape Canaveral Air Force Station (CCAFS), Florida. The 20 acre plume consists primarily of cis-1,2-dichloroethene (cis- DCE) and vinyl chloride, with remnants of trichloroethene (TCE) and tetrachloroethene in the suspect source area. The plume's distal end approaches the Banana River Lagoon, an Outstanding Florida Water with a zero degradation standard. The U.S. Air Force and its regulatory Partnering Team established objectives of reducing the dissolved contaminant levels to: (1) mitigate the long-term potential for releases to the lagoon and (2) restore the groundwater resource. Bioremediation was the selected strategy because it was compatible with implementation in the highly developed industrial area at the head of the plume and with the sensitive ecological zone at its toe. The local environmental chemistry and native microbial population were assessed prior to technology selection. While specific degraders were present, nutrient deficiencies were identified that may have contributed to slow conversion from DCE and vinyl chloride to non-toxic products. This information guided selection of amendments and the decision to bioaugment a portion of the site. Application of vegetable oil and nutrients (to supply nitrogen and phosphorus), supplemented by bioaugmentation, was implemented at Facility 60600 in the second half of 2006. Vegetable oil, monoammonium phosphate (MAP) and KB-1? Dechlorinator (a strain of Dehalococcoides ethenogenes (Dhc)) were injected into the area where cis-DCE concentrations were > 10,000 μg/L, vinyl chloride was > 4,000 μg/L and TCE or tetrachloroethene concentrations were > 1,000 μg/L. Encircling that area, where cis-DCE concentrations were > 4,000 μg/L, MAP only was added. Post-treatment groundwater monitoring showed a significant increase in Dhc populations in the area where MAP only was added. Approximately one year after the initial treatment event, MAP was again applied, with bioaugmentation at select locations. Between the two events, 31,000 gallons of vegetable oil and 3,100 pounds of MAP were injected hydraulically into an area of approximately 63,500 s.f. Over either a 20–30 or 25–45 ft. Below ground surface (bgs) interval. A total of 270 liters of KB-1? Was slipstreamed in with the vegetable oil and nutrient injections. Performance monitoring results have shown both cis-DCE and vinyl chloride levels across the area initially treated with vegetable oil, MAP and KB-1? Reduced by orders of magnitude. In monitoring wells through the axis of the treatment areas, post-treatment cis-DCE now fluctuates near its cleanup target level of 70 μg/L, down from a maximum
机译:正在应用生物刺激和生物沉默技术来对佛罗里达州Canaveration空军站(CCAFS)的设施60600进行溶解的卤代碳羽流。 20英亩的羽毛主要由Cis-1,2-二氯乙烯(CIS-DCE)和氯乙烯组成,在嫌疑源区中具有三氯乙烯(TCE)和四氯乙烯的残余物。羽流的远端接近香蕉河泻湖,这是一个杰出的佛罗里达水,具有零退化标准。美国空军及其监管合作团队建立了将溶解的污染水平降低至:(1)减轻泻湖和(2)恢复地下水资源的长期潜力。生物修复是选定的策略,因为它与羽流头部高度发达的工业区的实施兼容,脚趾敏感生态区。在技​​术选择之前评估当地的环境化学和本机微生物群。虽然存在特异性降解剂,但鉴定了营养缺陷,其可能导致从DCE和氯乙烯转化为无毒产物。该信息引导了修正案的选择和决定生物构建本网站的一部分。植物油和营养素的应用(供应氮气和磷),在2006年下半年的设施60600中实施了生物沉积。植物油,磷酸甘油铵(MAP)和KB-1?将脱氯剂(将脱卤素血管原(DHC))注射到CIS-DCE浓度>10,000μg/ L,氯乙烯>4,000μg/ L和TCE或四氯乙烯浓度>1,000μg/升的区域中。环绕该区域,其中CIS-DCE浓度>4,000μg/ L,仅加入图。治疗后地下水监测显示该地区仅添加地图的DHC群体显着增加。在初始治疗事件后大约一年,地图再次应用地图,在选择位置进行生物沉默。在两种事件之间,31,000加仑的植物油和3,100磅的地图被液压进入约63,500 s.f.超过20-30或25-45英尺。地面(BGS)间隔下方。共有270升的KB-1?用植物油和营养注射液流着。性能监测结果表明,含有植物油,地图和KB-1最初处理的区域的顺式DCE和氯乙烯水平?减少了数量级。在通过治疗区域的轴线监测孔中,处理后CIS-DCE现在在其清除目标水平靠近70μg/ l的近似波动,从最大值下降

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