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In Situ Oxidation of 1,4-Dioxane with Persulfate-Based Oxidation Activated by Iron Minerals

机译:铁矿物活化过硫酸盐基氧化原位氧化1,4-二恶烷

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摘要

Groundwater contaminant plumes of 1,4-dioxane (dioxane) and its co-contaminants (chlorinated solvents) have been found at many hazardous waste sites. There is increasing attention paid to the persulfate-based activation method for in situ degradation of organic contaminants due to its high efficiency and low cost. Iron mineral-based remediation methods, such as siderite and natural aquifer geomedia, have been of sustained interest due to their potential to activate oxidants in situ without the addition of extra activation chemical into the subsurface. However, very few studies have investigated the effectiveness of persulfate-based activation by natural aquifer materials, and these few studies have focused on oxidant activation and not on the efficacy of contaminant degradation nor on dioxane compounds specifically. Hydrogen peroxide is another promising oxidants with high oxidation potential. The effectiveness is well demonstrated when applying it individually. However, the combined system of activated hydrogen peroxide and persulfate are poorly understood. The combination of the two oxidants has the potential to enhance the transport of oxidant and their distribution across larger radii. In addition, co-occurrence of dioxane with chlorinated-solvent compounds and the influence of groundwater constituents are also very important for site application.;One objective of the current study is to investigate the capacity of natural soils and sediments to activate a binary persulfate/peroxide system to specifically enhance in-situ degradation of dioxane. Batch and column experiments are conducted with four natural geomedia. The results indicate the selected subsurface media could successfully induce activation of oxidant, which led to enhanced dioxane degradation. The oxidation-enhancement potential of the four geomedia used herein varied primarily due to the magnitude of available sediment-phase iron, and possibly with minor contribution of manganese oxides and soil organic matter. An alternative remediation method for sites at which the natural sediment does not have sufficient activation capacity is to use a permeable reactive barrier (PRB). However, the standard PRB, which employs iron filings as the reactive medium, are generally not effective for treating dioxane. The potential of the iron-filings-based PRB supplemented with persulfate--based oxidation for combined oxidative-reductive removal of dioxane from groundwater was evaluated in this study. The feasibility was proved by the successful activation of persulfate and facilitation of dioxane degradation using iron filings in both batch and column experiments. Approximate transport distances required to achieve a targeted degree of dioxane degradation can be estimated using the measured rate coefficients and groundwater velocity at the plume scale.;It is shown by this research that both ferrous ion and alkaline condition can activate the binary oxidant hydrogen peroxide-persulfate system to degrade dioxane. However, ferrous ion was significantly more effective than alkaline due to the different activation mechanism. Ferrous ion directly catalyzed the decomposition of hydrogen peroxide and persulfate and generated hydroxyl and sulfate radicals with high oxidation potential. In contrast, it is hypothesized that under alkaline conditions, hydroxyl and sulfate radicals were generated via the reactions between hydrogen peroxide/persulfate and an intermediate ion, hydroperoxide anion, which decreased effective production of radicals. The degradation rate of dioxane by the activated binary hydrogen peroxide-persulfate system was slower in the presence of groundwater and typical groundwater constituents compared to ultrapure water. Chloride, sulfate, bicarbonate, potassium, calcium, and magnesium ions that are present in groundwater inhibited the oxidative degradation of dioxane. The inhibition was particularly strong for bicarbonate and calcium ions. Therefore, the scavenging effect of ions, especially critical for bicarbonate and calcium, may need to be considered during calculation of the total oxidant demand (TOD) when planning field scale applications.;Overall, the results of the study indicate that the persulfate-based oxidation activated by iron minerals is generally effective for treating dioxane alone and as a co-contaminant with TCE. The effectiveness of employing in situ activated in situ chemical oxidation (ISCO) will depend on numerous site-specific factors including groundwater hydraulics and contaminant concentrations in addition to geochemical properties of the geomedia and groundwater.
机译:在许多危险废物现场发现了地下​​水中的1,4-二恶烷(二恶烷)及其共污染物(氯化溶剂)羽状污染物。由于过硫酸盐基活化方法的高效率和低成本,因此日益引起人们的关注,该方法用于有机污染物的原位降解。铁矿石基修复方法(例如菱铁矿和天然含水层土工介质)一直备受关注,因为它们具有在原位活化氧化剂而不向地下添加额外活化剂的潜力。但是,很少有研究研究过天然含水层材料过硫酸盐活化的有效性,而这些研究很少集中在氧化剂的活化上,而不是在污染物降解的效力上,也不是在二恶烷化合物上。过氧化氢是另一种具有高氧化潜力的有前途的氧化剂。单独应用时,效果已得到充分证明。然而,对活化的过氧化氢和过硫酸盐的组合体系了解甚少。两种氧化剂的组合具有增强氧化剂的运输及其在更大半径范围内分布的潜力。此外,二恶烷与氯代溶剂化合物的共存以及地下水成分的影响对于现场应用也很重要。;本研究的一个目标是研究天然土壤和沉积物激活二元过硫酸盐/水的能力。过氧化物系统可专门增强二恶烷的原位降解。批处理和色谱柱实验是使用四种自然地理介质进行的。结果表明,所选的地下介质可以成功地诱导氧化剂的活化,从而导致二恶烷降解增强。本文使用的四种土工介质的增强氧化作用的潜力主要是由于可利用的沉积相铁的量而变化,并且可能是由于锰氧化物和土壤有机质的贡献较小。对于天然沉积物没有足够活化能力的场所,另一种补救方法是使用可渗透反应性屏障(PRB)。但是,采用铁屑作为反应介质的标准PRB通常不能有效地处理二恶烷。在这项研究中,评估了铁基PRB补充过硫酸盐基氧化对地下水中二恶烷的氧化还原联合去除的潜力。批处理和色谱柱实验中使用铁屑成功活化了过硫酸盐并促进了二恶烷降解,证明了可行性。可以使用测得的速率系数和羽状尺度的地下水速度来估算达到目标二恶烷降解程度所需的近似运输距离。;这项研究表明,亚铁离子和碱性条件均可激活二元氧化剂过氧化氢,过硫酸盐体系降解二恶烷。然而,由于不同的活化机理,亚铁离子比碱金属明显更有效。亚铁离子直接催化过氧化氢和过硫酸盐的分解,并生成具有高氧化电位的羟基和硫酸根。相反,假设在碱性条件下,通过过氧化氢/过硫酸氢盐和中间离子氢过氧化物阴离子之间的反应生成了羟基和硫酸根自由基,这降低了自由基的有效产生。与超纯水相比,在存在地下水和典型地下水成分的情况下,活化的过氧化氢-过硫酸氢盐二元体系对二恶烷的降解速度较慢。地下水中存在的氯离子,硫酸根,碳酸氢根,钾离子,钙离子和镁离子抑制了二恶烷的氧化降解。对碳酸氢根和钙离子的抑制作用特别强。因此,在计划田间规模应用时,可能需要在计算总氧化剂需求量(TOD)时考虑离子的清除作用,尤其是对于碳酸氢根和钙而言至关重要。总的来说,研究结果表明,基于过硫酸盐的由铁矿物质活化的氧化通常可有效地单独处理二恶烷并作为与TCE的共同污染物。采用原位活化的原位化学氧化(ISCO)的有效性将取决于许多特定地点的因素,包括地下水介质和污染物的浓度,以及地球介质和地下水的地球化学特性。

著录项

  • 作者

    Yan, Ni.;

  • 作者单位

    The University of Arizona.;

  • 授予单位 The University of Arizona.;
  • 学科 Hydrologic sciences.;Geochemistry.;Environmental science.
  • 学位 Ph.D.
  • 年度 2018
  • 页码 222 p.
  • 总页数 222
  • 原文格式 PDF
  • 正文语种 eng
  • 中图分类
  • 关键词

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