首页> 外文会议>1998 Joint Conference on the Environment, 1998, Mar 31-Apr 1, 1998, Albuquerque, NM >Control of Metals Contamination in Groundwater Using Iron-oxide-coated Sand and Magnetite-coated Sand
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Control of Metals Contamination in Groundwater Using Iron-oxide-coated Sand and Magnetite-coated Sand

机译:用氧化铁砂和磁铁矿砂控制地下水中的金属污染

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Many hazardous waste sites have more than a single contaminant. Groundwater contamination at wood preservative sites, in particular, often contains metals mixtures. Among common metals formulations used as wood preservatives are copper, chromium, and arsenic (CCA), and ammoniacal copper zinc arsenate (ACZA). Copper, zinc, chromate, and arsenate are toxic elements and potentially hazardous. The chemical properties of these metals in aqueous solution are quite different. Cu(Ⅱ) and Zn(Ⅱ) are cations and strongly adsorb on oxide surfaces in soils, while Cr(Ⅵ) and As(Ⅴ) are oxyanions and redox sensitive under environmental conditions. Cr(Ⅵ) species (as HCrO_4~- and CrO_4~(2-)) are the greatest environmental concern due to their toxicity and mobility, while Cr(Ⅲ) is less toxic and is removed from solution as the Cr(OH)_3~0 precipitated phase. Contrasting with chromium, the reduced forms of arsenic (As(Ⅲ), as HAsO_2 and AsO_2~-) are more toxic and mobile than the oxidized forms (As(Ⅴ), as HAsO_4~(2-) and H_2AsO_4~-). Metals can be removed from contaminated groundwater by adsorption and/or reduction onto iron-oxide minerals (e.g. hematite and biotite). Iron-oxide minerals are promising adsorbent materials for removal of low concentrations of heavy metals from contaminated groundwater (Benjamin and Leckie 1981). Iron-oxide-coated sand (IOCS) has been successfully used in our lab in both batch and column reactor experiments to remove Pb, Cr, Cu, and As from aqueous solution (Azizian and Nelson, 1997; Khaodhiar et al., 1998). The Fe(Ⅱ) component of selected iron oxides reacts with electroactive metals such as Cr(Ⅵ) to effect their reduction. Magnetite is a mixed oxidation state (ferrous-ferric) oxide, providing both adsorption arid reduction capabilities. Prepared as magnetite-coated-sand (MCS), it provides simultaneous removal of adsorbable and electroactive metals from aqueous solution, for example, Pb(Ⅱ) and Cr(Ⅵ). In mixed-metals contaminated ground waters (e.g. Cu(Ⅱ), Cr(Ⅵ), and As(Ⅴ)), MCS can be used to for simultaneous removal of Cu(Ⅱ) by adsorption, Cr(Ⅴ) by reduction to Cr(Ⅲ), and As(Ⅴ) by adsorption without reduction to As(Ⅲ). One possible advantage of MCS is that it adsorb As(V) and prevents it from reducing to the more toxic and mobile As(Ⅲ) species, compared to the metallic iron (Fe°), which is thermodynamically favorable for reduction of both Cr(Ⅵ) and As(Ⅴ). MCS and IOCS could be used for metals removal in a filter, a packed-bed reactor, or in a passive permeable barrier for wastewater and groundwater treatment.
机译:许多危险废物场所的污染物不止一种。特别是木材防腐场所的地下水污染通常包含金属混合物。用作木材防腐剂的常见金属配方包括铜,铬和砷(CCA),以及氨铜砷酸铜(ACZA)。铜,锌,铬酸盐和砷酸盐是有毒元素,并且有潜在危险。这些金属在水溶液中的化学性质完全不同。 Cu(Ⅱ)和Zn(Ⅱ)是阳离子,在土壤氧化物表面上有强吸附性,而Cr(Ⅵ)和As(Ⅴ)在环境条件下对氧阴离子和氧化还原敏感。 Cr(Ⅵ)种类(如HCrO_4〜-和CrO_4〜(2-))由于其毒性和迁移率而对环境的影响最大,而Cr(Ⅲ)的毒性较小,当Cr(OH)_3时从溶液中去除。 〜0沉淀相。与铬相反,砷的还原形式(As(Ⅲ),如HAsO_2和AsO_2〜-)比氧化形式的砷(As(Ⅴ),如HAsO_4〜(2-)和H_2AsO_4〜-)具有更高的毒性和移动性。可以通过吸附和/或还原到氧化铁矿物(例如赤铁矿和黑云母)上,从受污染的地下水中去除金属。铁氧化物矿物质是从污染的地下水中去除低浓度重金属的有前途的吸附材料(Benjamin和Leckie 1981)。氧化铁包覆的砂(IOCS)已成功用于我们实验室的间歇式和柱式反应器实验中,以从水溶液中去除Pb,Cr,Cu和As(Azizian和Nelson,1997; Khaodhiar等,1998)。 。选定的氧化铁的Fe(Ⅱ)成分与Cr(Ⅵ)等电活性金属发生反应,使其还原。磁铁矿是一种混合氧化态(三价铁)氧化物,具有吸附和还原的能力。制备为磁铁矿覆盖砂(MCS),可同时去除水溶液中的可吸附金属和电活性金属,例如Pb(Ⅱ)和Cr(Ⅵ)。在混合金属污染的地下水(例如Cu(Ⅱ),Cr(Ⅵ)和As(Ⅴ))中,MCS可用于通过吸附同时去除Cu(Ⅱ),还原为Cr去除Cr(Ⅴ)。 (Ⅲ)和As(Ⅴ)通过吸附而没有还原为As(Ⅲ)。 MCS的一个可能优点是,与金属铁(Fe°)相比,MCS吸附了As(V)并阻止了它还原为更具毒性和移动性的As(Ⅲ)物种,在热力学上有利于同时还原两种Cr( Ⅵ)和砷(Ⅴ)。 MCS和IOCS可用于过滤器,填充床反应器或被动渗透屏障中的金属去除,以用于废水和地下水处理。

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