Arsenic in refractory gold ore processing
DOI:
https://doi.org/10.31643/2021/6445.12Keywords:
refractory gold-bearing ores, arsenopyrite, gold recovery, arsenic, mobility.Abstract
With "easy" ores becoming diminished, extractive industries are now shifting towards difficult deposits. In the future, gold-arsenic-bearing refractory ores will represent a prime example of the type of ores that may become more typical sourse for global gold recovery operations. Mining and beneficiation of As-bearing ores inevitably produce As-bearing wastes, which exacerbate any natural As mobilization. The mobility of As is governed by the interplay of redox reactions, adsorption/desorption, ion exchange, precipitation/dissolution, and biotransformation. The dominant processes depend on local biogeochemical conditions of the media, such as pH, Eh, chemical composition, as well as the presence and intensity of biological activity. This article provides an overview of current research on arsenic contamination of the environment caused by mineralization, mining and extraction of gold on the example of specific gold deposits.
Downloads
References
Gasparrini,C. Gold and other precious metals: from ore to market.Springer –Verlag Berlin Heidelberg, 2012.
Kenzhaliyev B.K., Koizhanova A.K., Magomedov D.R., Kamalov E.M., Erdenova M.B., Abdyldaev N.N. (2020). A study of the biohydrometallurgical method for extracting gold from flotation tailings. // Metalurgija. 59, 4, 477 -480.
Yessengarayev Ye.K., Surimbayev B.N., Baimbetov B.S., Mamyachenkov S.V., Kanaly T.S. Ore treatment hydrogen peroxide during heap leaching of gold. Kompleksnoe Ispol’zovanie Mineral’nogo Syr’a = Complex Use of Mineral Resources = Mineraldik Shikisattardy Keshendi Paidalanu. 2021. No1(316), pp. 5-14. https://doi.org/10.31643/2021/6445.01
Seitkan, A., Lampronti, G. I., Widmer, R. N., Casati, N. P., & Redfern, S. (2020). Thermal behavior of iron arsenides under non-oxidizing conditions. // ACS Оmega, 5 (12), 6423-64287.https://doi.org/10.1021/acsomega.9b03928.
Drahota,P., Rohovec, J., Filippi,M., Mihaljevic,M., Rychlovsky, P.,Cerveny, V.and Pertold,Z. (2009). Mineralogical and geochemical controls of arsenic speciation and mobility under different redox conditionsin soil, sediment and water at the Mokrsko-West gold deposit, Czech Republic. // Science of the Total Environment, 10, 3372–3384.
Borba, R.P.,Figueiredo, B.R.,Rawlins, B.,and Matschullat,J. (2003).Geochemical distribution of arsenic in waters, sediments and weathered gold mineralized rocks from Iron Quadrangle, Brazil. // Environmental Geology, 1, 39–52.
Dove,P.M.and Rimstidt, J.D.(1985). The solubility andstability of scorodite, FeAsO4·H2O. // American Mineralogist, 7-8, 838–844.
Pfeifer, H-R.,Häussermann, A.,Lavanchy, J-C.and Halter,W. (2007). Distribution and behavior of arsenic in soils and waters in the vicinity of the former gold-arsenic mine of Salanfe, Western Switzerland. // Journal of Geochemical Exploration, 3, 121–134.
Torrance, K., Keenan, H.,Munk, L.A.and Hagedorn,B. (2012). Arsenic speciation and mobility in surface water at Lucky Shot Gold Mine, Alaska. // Environmental Geochemistry and Health, 6, 711–723.
Craw, D.,Chappell, D.,Reay, A.,and Walls,D. (2000).Mobilisation and attenuation of arsenic around gold mines, East Otago, New Zealand. // New Zealand Journal of Geology and Geophysics, 43, 373–383.
Haffert,L.and Craw,D. (2008). Processes of attenuation of dissolved arsenic downstream from historic gold mine sites, New Zealand. // Science of the Total Environment, 405, 286–300.
ANZECC and ARMCANZ. Australian and New Zealand guidelines for fresh and marine water quality. Volume 1. The guidelines, Australia and New Zealand Environment and Conservation Council and Agriculture and Resource Management Council of Australia and New Zealand, Canberra, Australia, 2000.
Indigenous and Northern Affairs Canada (2016), Giant Mine Remediation Project. Available from: https://www.aadnc-aandc.gc.ca/eng/1100100027364/1100100027365. Accessed 16 February 2016.
Walker, S.R., Jamieson, H.E., Lanzirotti, A., Hall, G.E.M., and Peterson, R.C. (2015). The effect of ore roasting on arsenic oxidation state and solid phase speciation in gold mine tailings. // Geochemistry: Exploration, Environment, Analysis, 4, 273–291.
Bromstad, M.J. The characterization, persistence, and bioaccessibility of roaster-derived arsenic in surface soils at Giant Mine, Yellowknife, NT. Master’s thesis, Queen’s University, Canada, 2011.
Jamieson,H.E. (2014). The legacy of arsenic contamination from mining and processing refractory gold ore at Giant Mine, Yellowknife, Northwest Territories, Canada. // Reviews in Mineralogy and Geochemistry, 1, 533–551.
Subbaraman, J.V.(2001). The mill tailings of Kolar gold mines. // Current science, 6, 631–632.
Foster, A.L.,Brown, G.E.,Tingle, T.N.and Parks,G.A. 1998. Quantitative arsenic speciation in mine tailings using X-ray absorption spectroscopy. // American Mineralogist, 83, 553–568.
Fukushi, K.,Sasaki, M.,Sato, T.,Yanase, N.,Amano, H.and Ikeda,H. (2003). A natural attenuation of arsenic in drainage from an abandoned arsenic mine dump. // Applied Geochemistry, 8, 1267–1278.
DeSisto, S.L.,Jamieson, H.E.and Parsons,M.B. (2011). Influence of hardpan layers on arsenic mobility in historical gold mine tailings. // Applied Geochemistry, 12, 2004–2018.
Meunier, L.,Walker, S.R.,Wragg, J.,Parsons, M.B.,Koch, I.,Jamieson, H.E.and Reimer,K.J. (2010). Effects of soil composition and mineralogy on the bioaccessibility of arsenic from tailings and soil in gold mine districts of Nova Scotia. // Environmental Science and Technology, 7, 2667–2674.
Downloads
Published
How to Cite
Issue
Section
License
Copyright (c) 2022 Seitkan, A., & Redfren, S.
This work is licensed under a Creative Commons Attribution-NonCommercial-NoDerivatives 3.0 Unported License.