Wazne Mahmoud, Jagupilla Santhi Chandra, Moon Deok Hyun, Christodoulatos Christos, Koutsospyros Agamemnon
Center for Environmental Systems, Stevens Institute of Technology, Castle Point on Hudson, Hoboken, NJ 07030, USA.
J Environ Qual. 2008 Oct 23;37(6):2125-34. doi: 10.2134/jeq2007.0443. Print 2008 Nov-Dec.
Batch leaching tests, qualitative and quantitative x-ray powder diffraction (XRPD) analyses, and geochemical modeling were used to investigate the leaching mechanisms of Cr(VI) from chromite ore processing residue (COPR) samples obtained from an urban area in Hudson County, New Jersey. The pH of the leaching solutions was adjusted to cover a wide range between 1 and 12.5. The concentration levels for total chromium (Cr) and Cr(VI) in the leaching solutions were virtually identical for pH values >5. For pH values <5, the concentration of total Cr exceeded that of Cr(VI) with the difference between the two attributed to Cr(III). Geochemical modeling results indicated that the solubility of Cr(VI) is controlled by Cr(VI)-hydrocalumite and Cr(VI)-ettringite at pH >10.5 and by adsorption at pH <8. However, experimental results suggested that Cr(VI) solubility is controlled partially by Cr(VI)-hydrocalumite at pH >10.5 and by hydrotalcites at pH >8 in addition to adsorption of anionic chromate species onto inherently present metal oxides and hydroxides at pH <8. As pH decreased to <10, most of the Cr(VI) bearing minerals become unstable and their dissolution contributes to the increase in Cr(VI) concentration in the leachate solution. At low pH ( <1.5), Cr(III) solid phases and the oxides responsible for Cr(VI) adsorption dissolve and release Cr(III) and Cr(VI) into solution.
采用分批浸出试验、定性和定量X射线粉末衍射(XRPD)分析以及地球化学建模,研究了从新泽西州哈德逊县市区获取的铬铁矿加工残渣(COPR)样品中Cr(VI)的浸出机制。将浸出溶液的pH值调节至1至12.5的较宽范围。对于pH值>5的情况,浸出溶液中总铬(Cr)和Cr(VI)的浓度水平实际上是相同的。对于pH值<5的情况,总Cr的浓度超过了Cr(VI)的浓度,两者之间的差异归因于Cr(III)。地球化学建模结果表明,在pH>10.5时,Cr(VI)的溶解度受Cr(VI)-水碳铝石和Cr(VI)-钙矾石控制,在pH<8时受吸附作用控制。然而,实验结果表明,在pH>10.5时,Cr(VI)的溶解度部分受Cr(VI)-水碳铝石控制,在pH>8时受水滑石控制,此外在pH<8时,阴离子铬酸盐物种会吸附到固有存在的金属氧化物和氢氧化物上。随着pH值降至<10,大多数含Cr(VI)的矿物变得不稳定,它们的溶解导致浸出液中Cr(VI)浓度增加。在低pH(<1.5)时,Cr(III)固相以及负责吸附Cr(VI)的氧化物溶解,并将Cr(III)和Cr(VI)释放到溶液中。