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Reactive Barriers for Containment of Metals-Contaminated Dredged Materials: Diffusion Studies

机译:遏制金属污染疏浚物料的无功屏障:扩散研究

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Heavy metals are a prevalent and tenacious contaminant in many sediments and dredged materials. Traditionally these contaminated sediments are moved to secure locations and capped with clean sediment materials in a confined aquatic disposal (CAD) cell. This technique relies upon the tortuosity and reactivity of the overlying clean sediments to inhibit metal diffusion. The use of reactive barriers in sediment caps offers the opportunity to actively adsorb and precipitate contaminants as they migrate from contaminated sediments, thus improving overall cap performance. Apatite minerals, such as fluorapatite [Ca_5(PO_4)_3F)], were evaluated as reactive barriers in a series of laboratory-scale diffusion experiments that took place over a period of 600 days. It was hypothesized that surface adsorption and precipitation would effectively bind diffusing heavy metals, preventing them from migrating past the reactive barrier. Diffusion models were used to determine barrier effects on effective diffusion coefficients (D_e). Decreases in diffusivity are attributed to adsorption/precipitation reactions in the presence of the apatite barriers. Reductions in average diffusivity for the most effective phosphate barrier (Florida apatite), when compared to a conservative control, were 91 % for Pb, 99.8% for Zn, 37% for Cr, and 57% for Cu. After diffusion, mineralogical analysis revealed several of the metal phosphate minerals in the reactive barrier material were highly stable apatite and tertiary metal phosphates including Pb_4O(PO_4)_2, ZnCr_(0.85)(PO_4)_2·xH_2O, Pb_3Cr(PO_4)_3, Pb_3Fe(PO_4)_3, Cd_5(PO_4)_3OH, and CaZn_2(PO_4)_2·H_2O. The presence of such metal phosphate minerals further indicates that Pb, Cd, and Zn had adsorbed to the reactive barrier mineral surfaces and reprecipitated as metal phosphates. The use of reactive barrier sediment caps reduces the environmental concerns associated with sediment disposal and may allow for beneficial reuse of dredged materials.
机译:重金属是许多沉积物和疏浚物料中普遍且顽强的污染物。传统上,这些受污染的沉积物被移动到固定位置并用狭窄的水生物处理(CAD)细胞中的清洁沉积物盖住。该技术依赖于覆盖清洁沉积物的曲折性和反应性来抑制金属扩散。在沉积物上使用反应性屏障在沉积物中具有主动吸附和沉淀污染物的机会,从而提高整体帽性能。磷灰石矿物质,例如氟磷酸盐[Ca_5(PO_4)_3F)],在一系列实验室级扩散实验中评估为在600天的一系列实验室级扩散实验中进行反应屏障。假设表面吸附和沉淀将有效地结合扩散重金属,防止它们迁移过反应屏障。扩散模型用于确定对有效扩散系数(D_E)的阻隔效应。扩散性降低归因于磷灰石屏障存在下的吸附/沉淀反应。与保守对照相比,对于最有效的磷酸盐屏障(佛罗里达磷灰石)的平均扩散性降低,Pb的91%,Zn的99.8%,Cr为37%,Cu的57%。扩散后,矿物学分析显示反应阻挡材料中的几种金属磷酸盐矿物质是高稳定的磷灰石和叔金属磷酸盐,包括Pb_4O(Po_4)_2,ZnCr_(0.85)(Po_4)_2·Xh_2O,PB_3CR(PB_4)_3,PB_3FE (PO_4)_3,CD_5(PO_4)_3OH,以及CAZN_2(PO_4)_2·H_2O。这种金属磷酸盐矿物的存在进一步表明Pb,Cd和Zn吸附到反应性阻挡矿物表面上并作为金属磷酸酯再沉淀。反应性屏障沉积物盖的使用减少了与沉积物处理相关的环境问题,并且可以允许疏浚物料的有益再利用。

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