Comparison of Efficiencies of Neutralizing Agents for Heavy Metal Removal from Acid Mine Drainage | ||
| Journal of Mining and Environment | ||
| مقاله 4، دوره 13، شماره 3، مهر 2022، صفحه 679-691 اصل مقاله (1.72 M) | ||
| نوع مقاله: Original Research Paper | ||
| شناسه دیجیتال (DOI): 10.22044/jme.2022.12090.2205 | ||
| نویسندگان | ||
| Afrodita Zendelska* 1؛ Adrijana Trajanova2؛ Mirjana Golomeova1؛ Blagoj Golomeov1؛ Dejan Mirakovski1؛ Nikolinka Doneva1؛ Marija Hadzi-Nikolova1 | ||
| 1Faculty of Natural and Technical Sciences, Goce Delchev University, Shtip, Republic of North Macedonia | ||
| 2Mine Bucim, Radovish, Republic of North Macedonia | ||
| چکیده | ||
| The treatment of acid mine drainages is usually based on two basic technologies, active and passive treatment technologies. Whichever acid mine drainage (AMD) treatment method is employed, a neutralizing procedure that raises the water's pH over 7.0 using alkaline agents is required prior to discharge. A comparison of eight different agents (BaCO3, Na2CO3, NaOH, KOH, K2CO3, MgO, CaCO3, and Ba(OH)2) was performed in order to choose the most effective neutralizing agent for acid mine drainage treatment. The experiments were performed using a multi-component synthetic aqueous solution with an initial concentration of 10 mg/L of the Cu, Mn, Zn, Fe, and Pb ions and an initial pH value of 1.9. According to the research, the most effective neutralizing agent for the removal of heavy metals from a multi-component aqueous solution is MgO, while the least effective agent was Na2CO3. The obtained series of effective neutralizing agents for the removal of heavy metals from a multi-component aqueous solution are presented in the work. The effect of the studied concentration of neutralizing agents depends on the neutralizing agents and heavy metals that are used. The percentage of heavy metals removed from aqueous solutions increases along with rising pH values. The consumption of the neutralizing agent decreases as the concentration of the neutralizing agent is increased. In addition, the time taken to achieve pH depends on the agent concentration. In particular, as the concentration of the neutralizing agent increases, the time to reach the pH decreases. | ||
| کلیدواژهها | ||
| heavy metals؛ soda ash؛ caustic soda؛ limestone؛ hydrated lime | ||
| مراجع | ||
|
[1]. Jenkins, D.A., Johnson, D.B., and Freeman, C. (2000). Mynydd Parys Cu-Pb-Zn mines: mineralogy, microbiology and acid mine drainage. In: Cotter-Howells, J.D., Campbell, L.S., Valsami-Jones, E., and Batchelder. M. (Editors.) Environmental mineralogy: microbial interactions, anthropogenic influences, contaminated land and waste management. The Mineralogy Society Series No. 9. Mineralogical Society, London, UK, 161-180.
[2]. Evangelou, V.P. (1998). Pyrite chemistry: the key for abatement of acid mine drainage. In: Geller, A., Klapper, H., and Salomons, W., Editors. Acidic Mining Lakes: Acid Mine Drainage, Limnology and Reclamation. Berlin: Springer; 197– 222.
[3]. Motsi, T. (2010). Remediation of acid mine drainage using natural zeolite, Doctotal thesis, United Kingdom: School of Chemical Engineering, The University of Birmingham.
[4]. Huyen, D., Tabelin, C., Thuan, H., Dang, D., Truong, P., Vonghuthone, B., Kobayashi, M., and Igarashi, T. (2019). The solid-phase partitioning of arsenic in unconsolidated sediments of the Mekong Delta, Vietnam and its modes of release under various conditions. Chemosphere 233, 512–523.
[5]. Igarashi, T., Herrera, P., Uchiyama, H., Miyamae, H., Iyatomi, N., Hashimoto, K., and Tabelin, C. (2020). The two-step neutralization ferrite-formation process for sustainable acid mine drainage treatment: Removal of copper, zinc and arsenic, and the influence of coexisting ions on ferritization. Sci. Total Environ. 715, 136877.
[6]. Skousen, J., Ziemkiewicz, P., and Mcdonald, L. (2019). Acid mine drainage formation, control and treatment: Approaches and strategies. Extr. Ind. Soc. 6, 241–249.
[7]. Turingan, C.O.A., Singson, G.B., Melchor, B.T., Alorro, R.D., Beltran, A.B., and Orbecido, A.H. (2020). Evaluation of Efficiencies of Locally Available Neutralizing Agents for Passive Treatment of Acid Mine Drainage. Minerals, 10, 845. https://doi.org/10.3390/min10100845
[8]. Penreath, R.J. (1994). The discharge of waters from active and abandoned mines. In: Hester, R.E. and Harrison, R.M. (Editors.) Mining and its environmental impact. Issues in Environmental Science and Technology No. 1. Royal Society of Chemistry, Herts, UK, 121-132.
[9]. Golomeova, M., Zendelska, A., Krstev, B., Golomeov, B., and Krstev, A. (2012) Mine drainage treatment. In: 4th Congress of ecologists of the Republic of Macedonia with international participation, 12-15 Oct. 2012, Ohrid, Macedonia.
[10]. Waters J.C., Santomartino S., Cramer M., Murphy N., and Taylor J.R. (2003). Acid rock drainage treatment technologies–identifying appropriate solutions. Proceedings, 6th International Conference on Acid Rock Drainage. 12–18 July, Cairns, Queensland, Australia. 831 843.
[11]. Coulton, R., Bullen, C., and Hallet, C. (2003). The design and optimization of active mine water treatment plants. Land Contamination and Reclamation, 11, 273–279.
[12]. Kefeni, K., Msagati, T., and Mamba, B. (2017). Acid mine drainage: Prevention, treatment options, and resource recovery: A review. J. Clean. Prod.
[13]. Park, I., Tabelin, C., Jeon, S., Li, X., Seno, K., Ito, M., and Hiroyoshi, N. (2019). A review of recent strategies for acid mine drainage prevention and mine tailings recycling. Chemosphere 219, 588–606.
[14]. Skousen, J.G., Sexstone, A., and Ziemkiewicz, P. (2000). Acid mine drainage control and treatment. Reclam. Drastically Disturb. Lands.
[15]. Skousen, J. and Ziemkiewicz, P. (2005). Performance of 116 passive treatment systems for acid mine drainage. In Proceedings of the 2005 National Meeting of the American Society of Mining and Reclamation, Breckenridge, CO, USA, 19–23 June 2005.
[16]. Muliwa, A. and Leswifi, T. (2018). Performance evaluation of eggshell waste material for remediation of acid mine drainage drom coal dump leachate. Miner. Eng. 122, 241–250.
[17]. Heviánková, S. and Bestová, I. (2014). The application of wood ash as a reagent in acid mine drainage treatment. Miner. Eng. 56, 109–111.
[18]. Ouakibi, O. and Hakkou, R. (2014). Phosphate carbonated wastes used as drains for acidic mine drainage passive treatment. Procedia Eng. 83, 407–414.
[19]. Kamal, N.M. and Sulaiman, S.K. (2014). Bench-Scale study of acid mine drainage treatment using local neutralisation agents. Malays. J. Fundam. Appl. Sci. 10, 150–153.
[20]. Trumm, D. (2010). Selection of active and passive treatment systems for AMD—flow charts for New Zealand conditions, New Zealand Journal of Geology and Geophysics, 53:2-3, 195-210, DOI: 10.1080/00288306.2010.500715
[21]. Loza, N. and Aduvire, O. Acid Mine Drainage Treatment Process Optimization for Manganese Content Reduction by Sequential Neutralization. Available at: https://www.srk.com/en/publications/acid-mine-drainage-treatment-process-optimization-for-manganese-content-reduction-by-sequential-neut
[22]. Kapil, N. and Bhattacharyya, K.G. (2017). A comparison of neutralization efficiency of chemicals with respect to acidic Kopili River water, Appl Water Sci (2017) 7:2209–2214, DOI 10.1007/s13201-016-0391-6
[23]. Turingan, C., Singson, G., Melchor, B., Alorro, R., Beltran, A., and Orbecido, A. (2020). A comparison of the acid mine drainage (AMD) neutralization potential of low grade nickel laterite and other alkaline generating materials, IOP Conf. Series: Materials Science and Engineering 778, doi:10.1088/1757-899X/778/1/012142
[24]. Skousen, J.G. Sexstone, A., and Ziemkiewicz, P.F. (2000). Acid mine drainage control and treatment, Chapter 6. Reclamation of Drastically Disturbed Lands, American Society of Agronomy and American Society for Surface Mining and Reclamation. Volume No. 41. https://doi.org/10.2134/agronmonogr41.c6
[25]. Skousen, J., Zipper, C.E., Rose, A., Ziemkiewicz, P.F., Nairn, R., McDonald, L.M., and Kleinmann R.L. (2017). Review of Passive Systems for Acid Mine Drainage Treatment, Mine Water Environ (2017) 36:133–153, DOI 10.1007/s10230-016-0417-1
[26]. Bologo, V., Maree, J.P., and Carlsson, F. (2012). Application of magnesium hydroxide and barium hydroxide for the removal of metals and sulphate from mine water, Water SA Vol. 38 No. 1, http://dx.doi.org/10.4314/wsa.v38i1.4
[27]. Maila, M.D., Maree, J.P., and Cele, L.M. (2014). Acid mine water neutralisation with ammonium hydroxide and desalination with barium hydroxide, Water SA Vol. 40 No. 3, http://dx.doi.org/10.4314/wsa.v40i3.16
[28]. Masindi V., Akinwekomi V., Philippus M.J., and Lilith M.K. (2017). Efficiencies of different alkaline generating agents for the treatment of acid mine drainage: A comparative study and techno-economic appraisals, Mine Water and Circular Economy, Lappeenranta, Finland.
[29]. Masindi V., Akinwekomi V., Maree J.P., and Muedi K.L. (2017). Comparison of mine water neutralisation efficiencies of different alkaline generating agents, Journal of Environmental Chemical Engineering, Vol 5 (4), 3903-3913, https://doi.org/10.1016/j.jece.2017.07.062.
[30]. Potgieter-Vermaak S.S., Potgieter J.H., Monama P., and Van Grieken R. (2006). Comparison of limestone, dolomite and fly ash as pre-treatment agents for acid mine drainage, Minerals Engineering, Vol. 19 (5), 454-462, https://doi.org/10.1016/j.mineng.2005.07.009. | ||
|
آمار تعداد مشاهده مقاله: 417 تعداد دریافت فایل اصل مقاله: 675 |
||