Abiotic transformation of chlorinated aliphatic ground water contaminants: characterization of mineral reaction products

氯化脂肪族地下水污染物的非生物转化：矿物反应产物的表征

• 批准号: 1033836
• 负责人: Elizabeth Butler
• 金额: $ 32.94万
• 依托单位: University of Oklahoma Norman Campus
• 依托单位国家: 美国
• 项目类别: Continuing Grant
• 财政年份: 2010
• 资助国家: 美国
• 起止时间: 2010-10-01 至 2015-09-30
• 项目状态: 已结题
• 来源: https://www.nsf.gov/awardsearch/showAward?AWD_ID=1033836&HistoricalAwards=false
• 关键词: Abiotic; transformation; chlorinated; aliphatic; ground

PI: Elizabeth ButlerProposal Number: CBET-1033836Institution: University of OklahomaTitle: Abiotic transformation of chlorinated aliphatic ground water contaminants: characterization of mineral reaction productsGround water contaminants such as tetrachloroethylene (PCE), trichloroethylene (TCE), and carbon tetrachloride (CT) have the potential to adversely impact the health of U.S. citizens due to their widespread occurrence at contaminated sites. Numerous studies have shown that abiotic minerals containing ferrous iron and/or sulfide can transform these compounds, sometimes to reaction products that are completely nontoxic. Mineral mediated abiotic transformations can be used in remediation technologies such as in situ reactive zones and monitored natural attenuation. While the organic products of PCE, TCE, and CT transformation by minerals have been well characterized, the products that form when the minerals are oxidized by contaminants such as PCE, TCE, and CT have not been well studied and are the focus of this research. The overall objective of the research is to characterize the solid phase products that form upon mineral oxidation by chlorinated aliphatic contaminants, and to assess the potential for regeneration of reactive minerals under natural or engineered conditions. Two minerals (iron sulfide (FeS)) and chloride green rust (GR-Cl, a mixed valence iron oxide) and three model contaminants (PCE, TCE, and CT) will be studied. The specific objectives of the research are to: (1) characterize the rates of FeS and GR-Cl oxidation by PCE, TCE, and CT; (2) identify the mineral-associated products of FeS and GR-Cl oxidation by these contaminants; and (3) assess whether FeS and GR-Cl can be regenerated in the presence of abiotic reductants (for FeS) and/or bacteria (for FeS and GR-Cl) in batch and flow through systems. Batch experiments will be carried out in flame sealed glass ampules containing anoxic slurries of minerals and contaminants. Solid phase products of mineral transformation will be monitored by X-ray diffraction, X-ray photoelectron spectroscopy, and scanning electron microscopy with X-ray analysis. Dissolved products of mineral transformation will be monitored by analysis of Fe(II), S(-II), and chromium (II) reducible or ?extractable? sulfur (CrES), which includes elemental sulfur and polysulfides. After batch experiments are complete, they will prepare postage-stamp-sized chips of poly(methyl methacrylate) (Plexiglass) coated with mineral powders and place them in soil columns under flow through conditions. Then, they will monitor the solid phase and dissolved products of mineral oxidation by PCE, TCE, and CT, and the regeneration of reactive mineral species in the presence of bacteria, all under flow through conditions. The Plexiglass supports will allow them to place the reactive minerals in direct contact with soil and bacteria in such a way that we can subsequently extract them and monitor mineralogical changes that occur upon oxidation by PCE, TCE and CT.The research proposed here will enable more accurate long term application of remediation technologies involving abiotic minerals such as in situ reactive zones. This will benefit the many Americans who live in population centers that also contain high concentrations of sites with ground water contamination. In addition to these direct impacts, educational materials on abiotic remediation of ground water contaminants, suitable for undergraduate and graduate classes, will be developed based on the research results and submitted to the NSF K-Gray Engineering Pathway Digital Library. These materials will be widely promoted through professional organizations, and will help to fill a gap in current college textbooks. Undergraduate and graduate students will participate in this research, thereby preparing for careers in environmental engineering education and practice. Research results will be disseminated at scientific meetings attended by both researchers and practitioners, and will be published in widely read journals in the field.

主要研究者：Elizabeth Butler提案编号：CBET-1033836机构：俄克拉荷马大学标题：氯化脂肪族地下水污染物的非生物转化：矿物反应产物的表征地下水污染物，如四氯乙烯（PCE），三氯乙烯（TCE）和四氯化碳（CT）有可能对美国的健康产生不利影响.公民由于他们在污染场地的广泛发生. 许多研究表明，含有亚铁和/或硫化物的非生物矿物可以转化这些化合物，有时转化为完全无毒的反应产物。 矿物介导的非生物转化可用于补救技术，如原位反应区和监测自然衰减。 虽然PCE、TCE和CT通过矿物转化的有机产物已经得到很好的表征，但是当矿物被污染物如PCE、TCE和CT氧化时形成的产物还没有得到很好的研究，并且是本研究的焦点。 研究的总体目标是表征氯化脂肪族污染物氧化矿物后形成的固相产物，并评估在自然或工程条件下活性矿物再生的潜力。将研究两种矿物（硫化铁（FeS））和氯化物绿色锈（GR-Cl，一种混合价态氧化铁）以及三种模型污染物（PCE、TCE和CT）。 本研究的具体目标是：（1）通过PCE、TCE和CT表征FeS和GR-Cl氧化的速率;（2）通过这些污染物识别FeS和GR-Cl氧化的矿物相关产物;以及（3）评估在非生物还原剂（FeS）和/或细菌（FeS和GR-Cl）存在下，FeS和GR-Cl是否可以在批次和流通系统中再生。 分批实验将在装有矿物和污染物的缺氧泥浆的火焰密封玻璃安瓿中进行。 矿物转化的固相产物将通过X射线衍射、X射线光电子能谱和扫描电子显微镜及X射线分析进行监测。 矿物转化的溶解产物将通过分析Fe（II），S（-II）和铬（II）可还原或？可提取的？ 硫（克雷斯），其包括元素硫和多硫化物。 批量实验完成后，他们将准备邮票大小的聚（甲基丙烯酸甲酯）（有机玻璃）芯片涂有矿物粉末，并将它们放置在土壤柱下流过条件。 然后，他们将通过PCE，TCE和CT监测固相和矿物氧化的溶解产物，以及在细菌存在下反应性矿物物种的再生，所有这些都在流通条件下进行。 有机玻璃支持将使他们能够将活性矿物直接与土壤和细菌接触，这样我们就可以随后提取它们并监测PCE，TCE和CT氧化后发生的矿物学变化。这里提出的研究将使涉及非生物矿物的修复技术更准确的长期应用，如原位反应区。这将使许多居住在人口中心的美国人受益，这些人口中心也包含高浓度的地下水污染地点。 除了这些直接影响，地下水污染物的非生物修复教育材料，适合本科生和研究生班，将根据研究结果开发，并提交给NSF K-Gray工程途径数字图书馆。 这些材料将通过专业组织广泛推广，并将有助于填补目前大学教科书的空白。 本科生和研究生将参与这项研究，从而为环境工程教育和实践的职业生涯做好准备。 研究结果将在研究人员和从业人员参加的科学会议上传播，并将在该领域广泛阅读的期刊上发表。