首页> 外文会议>1998 Joint Conference on the Environment, 1998, Mar 31-Apr 1, 1998, Albuquerque, NM >Feasibility of Surfactant Use for In Situ Removal of Heavy Metals from Soil
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Feasibility of Surfactant Use for In Situ Removal of Heavy Metals from Soil

机译:使用表面活性剂现场去除土壤中重金属的可行性

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One of the most widespread problems confronted in environmental cleanup is heavy metal contaminated soil. This is exemplified in a report from the U. S. Department of Energy (Riley et al., 1992) which noted that 40% of the waste sites on DOE facilities had soils affected with heavy metals. When found in the environment at high concentrations, the toxicity of metals, such as lead, cadmium, and copper, pose a significant health risk to both animals and humans. Leachate and runoff from soils contaminated with heavy metals potentially degrade both ground and surface waters. Also of concern is wind erosion, which tends to spread contamination over expanded areas. Present technologies for in situ environmental remediation of metals from soil are costly and often ineffective. Consequently, new methods need to be developed. According to the United States Environmental Protection Agency (1997). the most promising new in situ technologies include electrokinetics, phytoremediation, solidification/stabilization, and soil flushing. Soil flushing with surfactants may be an effective and economically attractive alternative. This study focused on the feasibility of using surfactants to remove heavy metals from soils. The effectiveness of anionic and cationic surfactants, in particular, were compared with the capability of other soil flushing treatments. The amount of research conducted on surfactant enhanced in situ environmental remediation of heavy metals has to date been very limited. Competitive adsorption at soil cation exchange sites and pH adjustment are the dominant mechanisms for cationic surfactants. Batch equilibrium tests done by several researchers show cationic surfactants, especially at low pH conditions, to be effective in desorbing divalent lead, cadmium, copper, and zinc metal cations (Pb~(-2), Cd~(-2), Cu~(-2), and Zn~(-2)) from soil particles (Beveridge and Pickering. 1983: Westall et al., 1994). Colloid mobilization, soluble complex formation, and pH adjustment are the three processes by which anionic surfactants remove cationic heavy metal contaminants from soil. Carleson and Moussavi (1988) found the anionic surfactant, sodium dodecyl sulfate, to be an effective chelating agent for Zn~(-2), while Tan et al. (1994) isolated a naturally occurring anionic biosurfactant capable of forming a soluble complex with Cd~(-2), Coarse grained soils and aquifer material commonly contain significant amounts of clay mineral and/or organic colloids which adhere to the surfaces of larger sand grains (Muecke, 1979). Due to their substantial charge density and specific surface area, these colloids provide a preferential location for electrostatic adsorption of heavy metals. Allred and Brown (1995) have shown several anionic surfactants to be extremely effective in mobilization of colloids present in a sandy soil. Initial screening of 13 surfactants and 7 other flushing agents was accomplished using falling-head permeability tests on a sandy soil treated with lead nitrate. Next, batch tests and saturated column experiments on a contaminated sandy soil obtained from a mining site in northern New Mexico were conducted using the best of the screened surfactants along with disodium ethylene diamine tetraacetic acid and nitric acid.
机译:环境净化面临的最普遍问题之一是重金属污染土壤。美国能源部的一份报告(Riley等人,1992)对此进行了举例说明,该报告指出,DOE设施中40%的垃圾场都受到重金属污染。当在环境中以高浓度发现时,铅,镉和铜等金属的毒性对动物和人类均构成重大健康风险。受重金属污染的土壤的渗滤液和径流有可能使地下水和地表水退化。同样值得关注的是风蚀,它倾向于将污染扩散到更大的区域。目前用于土壤中金属原位环境修复的技术成本高昂,而且通常无效。因此,需要开发新的方法。根据美国环境保护局(1997)。最有前途的新技术包括电动学,植物修复,固化/稳定化和土壤冲洗。用表面活性剂冲洗土壤可能是一种有效且经济上有吸引力的选择。这项研究集中于使用表面活性剂去除土壤中重金属的可行性。尤其将阴离子和阳离子表面活性剂的功效与其他土壤冲洗处理的能力进行了比较。迄今为止,对表面活性剂增强原位环境修复重金属的研究数量非常有限。竞争性吸附在土壤阳离子交换位点和调节pH是阳离子表面活性剂的主要机理。几位研究人员进行的批平衡测试表明,阳离子表面活性剂,尤其是在低pH条件下,能有效地解吸二价铅,镉,铜和锌金属阳离子(Pb〜(-2),Cd〜(-2),Cu〜 (-2)和Zn〜(-2))(Beveridge and Pickering。1983:Westall et al。,1994)。胶体动员,可溶性复合物形成和pH调节是阴离子表面活性剂从土壤中去除阳离子重金属污染物的三个过程。 Carleson和Moussavi(1988)发现,阴离子表面活性剂十二烷基硫酸钠是Zn〜(-2)的有效螯合剂,而Tan等人。 (1994年)分离出一种天然阴离子生物表面活性剂,该表面活性剂能与Cd〜(-2)形成可溶性复合物。粗粒土壤和含水层材料通常包含大量黏土矿物和/或有机胶体,它们附着在较大的沙粒表面(Muecke,1979)。由于它们的大量电荷密度和比表面积,这些胶体为重金属的静电吸附提供了一个优先位置。 Allred and Brown(1995)已显示出几种阴离子表面活性剂,对沙质土壤中存在的胶体的迁移极为有效。使用落头渗透性测试在经过硝酸铅处理的沙质土壤上初步筛选了13种表面活性剂和7种其他冲洗剂。接下来,使用精选的最佳表面活性剂以及乙二胺二乙酸二钠和硝酸,对从新墨西哥州北部某矿场获得的受污染的沙质土壤进行了批处理试验和饱和柱实验。

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