Consolidation and incipient oxidation of alkaline arsenopyrite-bearing mine tailings, Macraes Mine, New Zealand

被引:21
作者
Craw, D
Chappell, D
Nelson, M
Walrond, M
机构
[1] Univ Otago, Dept Geol, Dunedin, New Zealand
[2] Univ Otago, Environm Sci Programme, Dunedin, New Zealand
关键词
D O I
10.1016/S0883-2927(98)00063-8
中图分类号
P3 [地球物理学]; P59 [地球化学];
学科分类号
0708 ; 070902 ;
摘要
Fine grained (ca. 15 mu m), arsenopyrite-bearing mine tailings have been exposed to drying and oxidation for 4 a pending relocation. The tailings are still partly covered by a pond of decanted pore waters. The water table in drying tailings has lowered by 1-3 m and desiccation cracks up to 2 cm wide have formed on the 1 m scale, extending through the unsaturated zone. Tailings in the unsaturated zone have similar pore water contents to saturated tailings: typically 16-32 wt% water. Saturated tailings retain alkaline pH (ca, 10) from the mine cyanidation plant, but pH lowers progressively towards ca. 7 near the surface, or near desiccation cracks, in the unsaturated zone. The redox state of the tailings changes in parallel with pH, with an empirical relationship: Eh(mV) = -55 pH + 290. Water in the remnant decant pond reflects this relationship also. Unsaturated tailings have variable but low permeabilities, typically 10(-3) to 10(-4) m/day, and more permeable horizons have allowed incursion of oxygenated air and/or rain water from desiccation cracks. Sulphide grains in all tailings examined are unaltered. Sulphides and solutions in the tailings are out of thermodynamic equilibrium predicted from the redox-pH conditions, due to kinetic constraints. Incursion of rain water locally facilitates deposition from pore waters of insoluble Fe oxide and arsenate minerals, thus fixing As in the dry unsaturated tailings. (C) 1999 Elsevier Science Ltd. All rights reserved.
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页码:485 / 498
页数:14
相关论文
共 19 条
[1]   LIMITS OF THE NATURAL ENVIRONMENT IN TERMS OF PH AND OXIDATION-REDUCTION POTENTIALS [J].
BECKING, LGMB ;
KAPLAN, IR ;
MOORE, D .
JOURNAL OF GEOLOGY, 1960, 68 (03) :243-284
[2]   Mine waste dumps and heavy metal pollution in abandoned mining district of Boccheggiano (Southern Tuscany, Italy) [J].
Benvenuti, M ;
Mascaro, I ;
Corsini, F ;
Lattanzi, P ;
Parrini, P ;
Tanelli, G .
ENVIRONMENTAL GEOLOGY, 1997, 30 (3-4) :238-243
[3]   SORPTION OF ARSENIC BY IRON-OXIDES AND OXYHYDROXIDES IN SOILS [J].
BOWELL, RJ .
APPLIED GEOCHEMISTRY, 1994, 9 (03) :279-286
[4]   ARSENIC SPECIATION IN SOIL POREWATERS FROM THE ASHANTI MINE, GHANA [J].
BOWELL, RJ ;
MORLEY, NH ;
DIN, VK .
APPLIED GEOCHEMISTRY, 1994, 9 (01) :15-22
[5]  
CHERRY JA, 1986, MIN ENERGY RES, V29, P1
[6]   APPLICATION OF A MASS-BALANCE MODEL TO ASSESS IN-PLACE ARSENIC POLLUTION [J].
DIAMOND, ML .
ENVIRONMENTAL SCIENCE & TECHNOLOGY, 1995, 29 (01) :29-42
[7]  
FISHEL VC, 1942, USGS WATER SUPPLY PA, V887, P56
[8]  
Garrels R.M., 1965, Solutions, minerals, and equilibria
[9]  
MCKEAG SA, 1989, MINER DEPOSITA, V24, P124
[10]   PYRITE OXIDATION AT CIRCUMNEUTRAL PH [J].
MOSES, CO ;
HERMAN, JS .
GEOCHIMICA ET COSMOCHIMICA ACTA, 1991, 55 (02) :471-482