Paktunc Dogan, Foster Andrea, Laflamme Gilles
Canada Centre for Mineral and Energy Technology (CANMET), Mining and Mineral Sciences Laboratories, 555 Booth Street, Ottawa, Ontario K1A 0G1 Canada.
Environ Sci Technol. 2003 May 15;37(10):2067-74. doi: 10.1021/es026185m.
Ketza River mine tailings deposited underwater and those exposed near the tailings impoundment contain approximately 4 wt % As. Column-leaching tests indicated the potential for high As releases from the tailings. The tailings are composed dominantly of iron oxyhydroxides, quartz, calcite, dolomite, muscovite, ferric arsenates, and calcium-iron arsenates. Arsenopyrite and pyrite are trace constituents. Chemical compositions of iron oxyhydroxide and arsenate minerals are highly variable. The XANES spectra indicate that arsenic occurs as As(V) in tailings, but air-drying prior to analysis may have oxidized lower-valent As. The EXAFS spectra indicate As-Fe distances of 3.35-3.36 A for the exposed tailings and 3.33-3.35 A for the saturated tailings with coordination numbers of 0.96-1.11 and 0.46-0.64, respectively. The As-Ca interatomic distances ranging from 4.15 to 4.18 A and the coordination numbers of 4.12-4.58 confirm the presence of calcium-iron arsenates in the tailings. These results suggest that ferric arsenates and inner-sphere corner sharing or bidentate-binuclear attachment of arsenate tetrahedra onto iron hydroxide octahedra are the dominant form of As in the tailings. EXAFS spectra indicate that the exposed tailings are richer in arsenate minerals whereas the saturated tailings are dominated by the iron oxyhydroxides, which could help explain the greater release of As from the exposed tailings during leaching tests. It is postulated that the dissolution of ferric arsenates during flow-through experiments caused the high As releases from both types of tailings. Arsenic tied to iron oxyhydroxides as adsorbed species are considered stable; however, iron oxyhydroxides having low Fe/As molar ratios may not be as stable. Continued As releases from the tailings are likely due to dissolution of both ferric and calcium-iron arsenates and desorption of As from high-As bearing iron oxyhydroxides during aging.
凯察河矿尾矿沉积于水下,而尾矿库附近暴露的尾矿含砷量约为4 wt%。柱浸试验表明尾矿有释放大量砷的可能性。尾矿主要由羟基氧化铁、石英、方解石、白云石、白云母、砷酸铁和钙铁砷酸盐组成。毒砂和黄铁矿为痕量成分。羟基氧化铁和砷酸盐矿物的化学成分变化很大。X射线吸收近边结构光谱表明尾矿中的砷以As(V)形式存在,但分析前的风干可能使低价砷发生了氧化。扩展X射线吸收精细结构光谱表明,暴露尾矿中砷与铁的距离为3.35 - 3.36 Å,饱和尾矿中为3.33 - 3.35 Å,配位数分别为0.96 - 1.11和0.46 - 0.64。砷与钙的原子间距离在4.15至4.18 Å之间,配位数为4.12 - 4.58,证实尾矿中存在钙铁砷酸盐。这些结果表明,砷酸铁以及砷酸根四面体以内层配位方式与氢氧化铁八面体的角共享或双齿双核连接是尾矿中砷的主要存在形式。扩展X射线吸收精细结构光谱表明,暴露尾矿中的砷酸盐矿物含量更高,而饱和尾矿以羟基氧化铁为主,这有助于解释浸出试验中暴露尾矿释放出更多砷的现象。据推测,在流通实验中砷酸铁的溶解导致了两种尾矿中砷的大量释放。与羟基氧化铁结合的吸附态砷被认为是稳定的;然而,铁/砷摩尔比低的羟基氧化铁可能不那么稳定。尾矿持续释放砷可能是由于砷酸铁和钙铁砷酸盐的溶解以及老化过程中高砷含量的羟基氧化铁对砷的解吸。