Heiderscheidt J L, Siegrist R L, Illangasekare T H
Environmental Science and Engineering Division, Center for Experimental Study of Subsurface Environmental Processes, Colorado School of Mines, Golden, CO 80401-1887, USA.
J Contam Hydrol. 2008 Nov 14;102(1-2):3-16. doi: 10.1016/j.jconhyd.2008.07.002. Epub 2008 Jul 11.
In situ chemical oxidation is a technology that has been applied to speed up remediation of a contaminant source zone by inducing increased mass transfer from DNAPL sources into the aqueous phase for subsequent destruction. The DNAPL source zone can consist of one or more individual sources that may be present as an interconnected pool of high saturation, as a region of disconnected ganglia at residual saturation, or as combinations of these two morphologies. Potassium permanganate (KMnO(4)) is a commonly employed oxidant that has been shown to rapidly destroy DNAPL compounds like PCE and TCE following second-order kinetics in an aqueous system. During the oxidation of a target DNAPL compound, or naturally occurring reduced species in the subsurface, manganese oxide (MnO(2)) solids are produced. Research has shown that these manganese oxide solids may result in permeability reductions in the porous media thus reducing the ability for oxidant to be transported to individual DNAPL sources. It can also occur at the DNAPL-water interface, decreasing contact of the oxidant with the DNAPL. Additionally, MnO(2) formation at the DNAPL-water interface, and/or flow-bypassing as a result of permeability reductions around the source, may alter the mass transfer from the DNAPL into the aqueous phase, potentially diminishing the magnitude of any DNAPL mass depletion rate increase induced by oxidation. An experiment was performed in a two-dimensional (2D) sand-filled tank that included several discrete DNAPL source zones. Spatial and temporal monitoring of aqueous PCE, chloride, and permanganate concentrations was used to relate changes in mass depletion of, and mass flux, from DNAPL residual and pool source zones to chemical oxidation performance and MnO(2) formation. During the experiment, permeability changes were monitored throughout the 2D tank and these were related to MnO(2) deposition as measured through post-oxidation soil coring. Under the conditions of this experiment, MnO(2) formation was found to reduce permeability in and around DNAPL source zones resulting in changes to the overall flow pattern, with the effects depending on source zone configuration. A pool with little or no residual around it, in a relatively homogeneous flow field, appeared to benefit from resulting MnO(2) pore-blocking that substantially reduced mass transfer from the pool even though there was relatively little PCE mass removed from the pool. In contrast, a pool with residual around it (in a more typical heterogeneous flow field) appeared to undergo increased mass transfer as MnO(2) reduced permeability, altering the water flow and increasing the mixing at the DNAPL-water interface. Further, the magnitude of increased PCE mass depletion during oxidation appeared to depend on the PCE source configuration (pool versus ganglia) and decreased as MnO(2) was formed and deposited at the DNAPL-water interface. Overall, the oxidation of PCE mass appeared to be rate-limited by the mass transfer from the DNAPL to aqueous phase.
原位化学氧化是一项已被应用的技术,旨在通过促使更多质量从难溶性液体(DNAPL)源转移到水相以便后续销毁,从而加速对污染源头区域的修复。DNAPL源头区域可能由一个或多个单独的源组成,这些源可能以高饱和度的相互连通的池状形式存在,以残余饱和度下不连续的节状区域形式存在,或者以这两种形态的组合形式存在。高锰酸钾(KMnO₄)是一种常用的氧化剂,已证明其在水体系中按照二级动力学能迅速销毁诸如全氯乙烯(PCE)和三氯乙烯(TCE)等DNAPL化合物。在目标DNAPL化合物或地下天然存在的还原态物质氧化过程中,会生成氧化锰(MnO₂)固体。研究表明,这些氧化锰固体可能导致多孔介质渗透率降低,从而降低氧化剂输送到各个DNAPL源的能力。它也可能发生在DNAPL - 水界面处,减少氧化剂与DNAPL的接触。此外,在DNAPL - 水界面处形成MnO₂,和/或由于源周围渗透率降低导致的水流绕过,可能会改变从DNAPL到水相的传质,潜在地减小氧化引起的任何DNAPL质量消耗速率增加的幅度。在一个二维(2D)装满沙子的水箱中进行了一项实验,该水箱包含几个离散的DNAPL源区。对水相中PCE、氯离子和高锰酸盐浓度进行空间和时间监测,以关联DNAPL残余和池状源区的质量消耗变化以及质量通量与化学氧化性能和MnO₂形成之间的关系。在实验过程中,对整个二维水箱的渗透率变化进行了监测,并且将这些变化与通过氧化后土壤取芯测量的MnO₂沉积相关联。在本实验条件下,发现MnO₂的形成会降低DNAPL源区及其周围的渗透率,从而导致整体流动模式发生变化,其影响取决于源区配置。在相对均匀的流场中,周围几乎没有或没有残余物的池似乎受益于由此产生的MnO₂孔隙堵塞,这大大减少了从池中传质,尽管从池中去除的PCE质量相对较少。相比之下,周围有残余物的池(在更典型的非均匀流场中)似乎随着MnO₂降低渗透率而经历传质增加,改变了水流并增加了DNAPL - 水界面处的混合。此外,氧化过程中PCE质量消耗增加的幅度似乎取决于PCE源配置(池状与节状),并且随着MnO₂在DNAPL - 水界面处形成和沉积而降低。总体而言,PCE质量的氧化似乎受从DNAPL到水相的传质限制。