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Bioaugmentation and Biostimulation forDissolved Plume Treatment at Facility 60600

机译:生物增强和生物刺激用于设施60600的溶羽治疗

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Biostimulation and bioaugmentation techniques are being applied to treata 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 tetrachloroethenein 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 itsregulatory Partnering Team established objectives of reducing the dissolved contaminantlevels to: (1) mitigate the long-term potential for releases to the lagoon and (2) restore thegroundwater resource. Bioremediation was the selected strategy because it was compatiblewith implementation in the highly developed industrial area at the head of the plumeand with the sensitive ecological zone at its toe.The local environmental chemistry and native microbial population were assessedprior to technology selection. While specific degraders were present, nutrient deficiencieswere identified that may have contributed to slow conversion from DCE and vinyl chlorideto non-toxic products. This information guided selection of amendments and thedecision to bioaugment a portion of the site. Application of vegetable oil and nutrients (tosupply nitrogen and phosphorus), supplemented by bioaugmentation, was implemented atFacility 60600 in the second half of 2006. Vegetable oil, monoammonium phosphate(MAP) and KB-1? Dechlorinator (a strain of Dehalococcoides ethenogenes (Dhc)) wereinjected into the area where cis-DCE concentrations were >10,000 μg/L, vinyl chloridewas >4,000 μg/L and TCE or tetrachloroethene concentrations were > 1,000 μg/L. Encirclingthat area, where cis-DCE concentrations were >4,000 μg/L, MAP only wasadded. Post-treatment groundwater monitoring showed a significant increase in Dhcpopulations in the area where MAP only was added. Approximately one year after theinitial 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 wereinjected hydraulically into an area of approximately 63,500 s.f. Over either a 20–30 or25–45 ft. Below ground surface (bgs) interval. A total of 270 liters of KB-1? Was slipstreamedin with the vegetable oil and nutrient injections.Performance monitoring results have shown both cis-DCE and vinyl chloride levelsacross the area initially treated with vegetable oil, MAP and KB-1? Reduced by orders ofmagnitude. In monitoring wells through the axis of the treatment areas, post-treatmentcis-DCE now fluctuates near its cleanup target level of 70 μg/L, down from a maximum
机译:生物刺激和生物强化技术正被用于治疗 卡纳维拉尔角空军基地60600工厂的溶解卤化碳羽 (CCAFS),佛罗里达州。 20英亩的烟羽主要由顺式1,2-二氯乙烯(顺式 DCE)和氯乙烯,以及残留的三氯乙烯(TCE)和四氯乙烯 在可疑来源区域。羽流的远端接近香蕉河泻湖, 具有零降解标准的杰出佛罗里达水。美国空军及其 监管合作团队确定了减少溶解污染物的目标 达到以下水平:(1)减轻排放到泻湖的长期潜力,以及(2)恢复 地下水资源。选择生物修复是因为它具有兼容性 并在烟柱顶部高度发达的工业区中实施 脚趾处有敏感的生态区。 对当地环境化学和本地微生物种群进行了评估 在选择技术之前。尽管存在特定的降解剂,但营养缺乏 已确定可能导致DCE和氯乙烯转化缓慢 去无毒产品。该信息指导选择修正案和 决定对网站的一部分进行生物加固。植物油和养分的应用(用于 供应氮和磷),并辅以生物强化。 2006年下半年的60600设施。植物油,磷酸一铵 (MAP)和KB-1?脱氯剂(一种Dehalococcoides ethenogenes(Dhc)菌株)是 注入顺式-DCE浓度> 10,000μg/ L氯乙烯 是> 4,000μg/ L,TCE或四氯乙烯浓度> 1,000μg/ L。包围 顺式-DCE浓度>的区域 4,000μg/ L,仅MAP为 添加。处理后的地下水监测显示Dhc显着增加 仅添加MAP的区域中的人口总数。约一年后 在最初的治疗事件中,再次应用了MAP,并在选定位置进行了生物增强。 在这两次事件之间,分别有31,000加仑植物油和3,100磅MAP 液压注入到大约63,500 s.f.的区域中超过20–30或 距地面(bgs)以下25-45英尺。总共270升KB-1?错落有致 在注入植物油和营养素的过程中。 性能监测结果显示了顺-DCE和氯乙烯水平 最初用植物油,MAP和KB-1处理过的区域?减少了 震级。在通过处理区域的轴线监视井时,进行后处理 cis-DCE现在在其清理目标水平70μg/ L附近波动,从最大值

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