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Iron nanoparticles: Reactions with lindane and the hexachlorocyclohexanes.

机译:铁纳米颗粒:与林丹和六氯环己烷的反应。

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摘要

This research demonstrated the efficacy of nanoscale zero-valent iron (nZVI) at both the bench and field scales. This emerging technology utilizes iron particles of up to 200 nanometers (nm) in diameter to degrade redox-amenable contaminants via surface-mediated reduction reactions. Under development since 1996, nZVI represents a promising new remediation approach due to its: (1) enhanced reactivity relative to microscale and granular irons, (2) subsurface mobility potential, and (3) superior field deployment capabilities.; In aqueous batch studies, nZVI degraded gamma-hexachlorocyclohexane (gamma-HCH), a notorious organochlorine pesticide also known as lindane, within 24--48 hours by a reductive dihaloelimination process yielding gamma-3,4,5,6 tetrachlorocyclohexene (gamma-TeCCH). Using a pseudo first-order model, the lindane half-life was approximately 5 hours versus 24 hours with less reactive microscale iron. Balances on chloride, the principal product, generally were in the range of 0.50--0.75.; High gamma-HCH concentration studies in 95% ethanol demonstrated that nZVI can degrade lindane via both dihaloelimination non-reductive dehydrohalogenation in which gamma-2,3,4,5,6-pentachlorocyclohexene (gamma-PeCCH) was the only intermediate. Biphenyl was detected as an end product in the reductive pathway while the trichlorobenzenes (TCBs) were identified as surface-associated products in the non-reductive pathway. Lindane half-lives typically ranged from 2--5 hours. Chloride balances in the reductive pathway were approximately 0.55--0.75 but only 0.30--0.40 in the non-reductive pathway.; Nanoscale iron also effectively treated HCH-contaminated groundwater obtained from a pesticides manufacturing site in Florida. Summed HCH isomer (i.e. SigmaHCH) half-lives ranged from 3--16 hours depending upon nZVI dose as compared to approximately 30 hours with mZVI. The HCH isomers were removed by nZVI with varying effectiveness as follows: gamma > alpha > delta > beta.; The first-ever nZVI field demonstration involved the injection of slurried nanoiron (2.5 kg dry weight nZVI), under gravity-feed conditions, into trichloroethene (TCE)-impacted groundwater at a Trenton, NJ manufacturing site. During the ten-week study, aqueous TCE concentrations in the test area were reduced by up to 96.5%. Elevated levels of methane, ethane, and ethene were also detected. Moreover, reactions between nZVI and water caused the groundwater oxidation-reduction potential (ORP) to decline by 100--400 mV while the pH increased 0.5--1.5 standard units, depending on proximity to the injection well.
机译:这项研究证明了在工作台规模和现场规模上,纳米级零价铁(nZVI)的功效。这项新兴技术利用直径最大为200纳米(nm)的铁颗粒,通过表面介导的还原反应降解可氧化还原的污染物。自从1996年开始开发以来,nZVI代表了一种有前途的新修复方法,因为它具有:(1)相对于微型铁和粒状铁的反应性增强;(2)地下迁移潜力,以及(3)出色的现场部署能力。在水性批处理研究中,nZVI通过还原二卤消除过程在24--48小时内降解了臭名昭著的有机氯农药γ-六氯环己烷(γ-HCH),产生了gamma-3,4,5,6四氯环己烯(gamma-HCH)。 TeCCH)。使用伪一阶模型,林丹的半衰期约为5小时,而反应性微量铁含量​​较低的则为24小时。主要产品氯化物的余量通常在0.50--0.75之间。在95%乙醇中的高γ-六氯环己烷浓度研究表明,nZVI可以通过二卤代消除非还原性脱卤化氢反应降解林丹,其中只有gamma-2,3,4,5,6-五氯环己烯(γ-PeCCH)。联苯在还原途径中被检测为最终产物,而三氯苯(TCB)在非还原途径中被鉴定为与表面相关的产物。林丹的半衰期通常为2--5小时。还原途径中的氯化物平衡约为0.55--0.75,但非还原途径中仅为0.30--0.40。纳米铁还有效处理了从佛罗里达州一家农药生产基地获得的六氯环己烷污染的地下水。取决于nZVI剂量,总的HCH异构体(即SigmaHCH)半衰期为3--16小时,而使用mZVI约为30小时。六氯环己烷异构体通过nZVI去除的效力不同,如下所述:γ>α>δ>β。 nZVI的首次现场演示涉及在新泽西州特伦顿的生产基地,在重力进料条件下,将浆料状的纳米铁(2.5千克干重nZVI)注入受三氯乙烯(TCE)影响的地下水中。在为期十周的研究过程中,测试区域中的三氯乙酸的浓度降低了96.5%。还检测到甲烷,乙烷和乙烯含量升高。此外,nZVI与水之间的反应导致地下水氧化还原电位(ORP)下降100--400 mV,而pH值增加0.5--1.5标准单位,具体取决于与注入井的距离。

著录项

  • 作者

    Elliott, Daniel W.;

  • 作者单位

    Lehigh University.;

  • 授予单位 Lehigh University.;
  • 学科 Engineering Environmental.
  • 学位 Ph.D.
  • 年度 2005
  • 页码 325 p.
  • 总页数 325
  • 原文格式 PDF
  • 正文语种 eng
  • 中图分类 环境污染及其防治;
  • 关键词

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