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Soil flushing pilot test in a landfill polluted with liquid organic wastes from lindane production

机译:对林丹生产中的液态有机废物污染的垃圾填埋场进行土壤冲洗中试

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摘要

Sites contaminated by Dense Non-Aqueous Liquid Phases (DNAPLs) containing chlorinated compounds are a ubiquitous problem caused by spills or the dumping of wastes with no concern for the environment. Their migration by gravity through the subsurface and their accumulation far below ground level make in-situ treatments the most appropriate remediation technologies. In this work, an aqueous solution containing a non-ionic and biodegradable surfactant was injected in the Sardas alluvial layer contaminated at some points with DNAPL (formed by a mixture of more than 28 chlorinated compounds) from lindane production. A volume of 5.28 m of an aqueous surfactant emulsion (13 g L ) was injected at 14.5 m b g.l in the permeable layer (gravel-sand), at a flow rate of 0.6 m h and the groundwater was monitored within a test cell (3.5 m radius) built The flow of the injected fluids in the subsurface was also evaluated using a conservative tracer, bromide (130 mg L ), added to the surfactant solution. Concentration of contaminants, chloride, bromide and surfactant, surface tension and conductivity were measured at the injection point and at three monitoring points over time. High radial dispersion was noticed resulting in high dilution of the injected fluids. The surfactant was not adsorbed in the soil during the injection time, the adsorption of the surfactant took place in the meantime (15 h) between its injection and the groundwater (GW) extraction. The concentration of chlorinated compounds dissolved from the soil in the surfactant aqueous phase when equilibrium was reached (about 850 mg L ) is related to the moderate average contamination of the soil in the test cell (about 1230 mg kg ). In contrast, the extraction of the free DNAPL in the altered marls layer was highly enhanced due to the addition of the surfactant. Finally, it was found that the surfactant and the contamination did not migrate from the capture zone.
机译:普遍存在的问题是由泄漏的或倾倒的废物引起的,其中含有氯化化合物的稠密非水液相(DNAPL)污染,而与环境无关。它们在重力作用下通过地下迁移并在远低于地面的条件下堆积,这使得原位处理成为最合适的修复技术。在这项工作中,将含有非离子和可生物降解的表面活性剂的水溶液注入到在某些点受到林丹生产中DNAPL(由28种以上氯化化合物的混合物形成)污染的Sardas冲积层中。将体积为5.28 m的表面活性剂水乳状液(13 g L)以14.5 mb gl的速度以0.6 mh的流速注入渗透层(砾石砂)中,并在测试室(3.5 m还使用添加到表面活性剂溶液中的保守示踪剂溴化物(130 mg L)评估了地下流体的流量。随着时间的推移,在注入点和三个监测点测量污染物,氯化物,溴化物和表面活性剂的浓度,表面张力和电导率。注意到高度的径向分散,导致注入流体的高度稀释。在注入期间表面活性剂没有吸附在土壤中,在注入表面活性剂和提取地下水(GW)之间的同时(15小时)内发生了表面活性剂的吸附。当达到平衡时,从土壤中溶解在表面活性剂水相中的氯化物浓度(约850 mg L)与测试池中土壤的中等平均污染(约1230 mg kg)有关。相反,由于添加了表面活性剂,大大增强了在改变的泥灰层中游离DNAPL的提取。最后,发现表面活性剂和污染物没有从捕获区迁移。

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