Can Alternative Tailings Disposal Become the Norm in Mining?

Total Page:16

File Type:pdf, Size:1020Kb

Can Alternative Tailings Disposal Become the Norm in Mining? 40 FILTRATION AND DRYING Can alternative tailings disposal become the norm in mining? New technology promises to reduce water, create a smaller environmental footprint and reduce long-term risks for mines By Amanda Adams, Principal, Mining at Stantec and Theo Gerritsen, principal geotechnical engineer, Stantec’s Global Tailings Group here is no doubt that the time tailings management is an una- Mining low grades of ore has resources extracted from voidable necessity at many mines. resulted in increased water use per Tmining are critical to our way unit of production. In some cases, of life. Likely, you’re reading this WATER, WATER, WATER the availability of water is one of the on your computer, smartphone, or What are the challenges associated greatest constraints on mine develop- tablet. Mining touches all our lives with conventional tailings? Well, ment. By optimizing water recovery, daily (in addition to metals used in it is all about water. Managing seep- ATD technologies promise to reduce electronics, think about that can of age from the tailings themselves, water use at mines. This is of great soda you are drinking, or the aggre- monitoring pore water pressure advantage in some settings, and in gate used to pave your driveway). within the tailings dams or designing others ATD technologies promise a The industry works hard to make sure facilities to safely store or pass flood smaller environmental footprint and the net impact is positive. However, events. Because such a significant reduced long-term risks. the waste associated with mining, quantity of water is added during both past and present, is an unavoid- mineral processing, ‘conventional’ ALTERNATIVE TAILING able result of conventional mineral tailings dams store the tailings as a DISPOSAL OPTIONS By optimising processing. In the future it may be slurry. Water within the tailing mate- When considering alternative tail- water recovery, possible to extract metals like cop- rial is either evaporated, migrates ings disposal there are three major ATD per and gold without crushing and as seepage or remains entrained types. Each has advantages and technologies grinding the ore down to fine parti- within the tailings impoundment. disadvantages. promise to cle size and adding considerable Removing water prior to disposal • Thickened tailing disposal: reduce water quantities of liquid, resulting in con- through various means is considered Tailing materials are “thickened” use at mines ventional tailings. But, at the present ‘alternative’ disposal. through the use of high-density or July/August 2021 www. .com 42 FILTRATION AND DRYING ATD technologies deep-cone thickeners to about promise to 60-70% solids so the material reduce water does not segregate upon deposi- use at mines tion. This can have some benefits with respect to permeability and lower seepage, along with the higher initial water recovery, allowing immediate reuse of a greater fraction of the process water. Advantages: improved water conservation with lower energy input required (compared to other meth- ods) the equipment is relatively com- mon and easier to procure and it is widely used (there is a lot of experi- ence with the technology) and thickening is a continuous process Disadvantages: potential limita- tation is more attractive in, and (as opposed to a batch process). tions for filtering at the scale of this aided by, a dry climate. It takes Disadvantages: the capital cost of project and the large required time and money to remove water the thickeners and, because the tail- CAPEX (both a thickener and filter from the tailings and you don’t ings is in slurry form, a sizeable dam press are required), higher operating want to be in an environment that is still required for containment. costs including the cost of operating will put it right back in. the filter plant and the added cost of • Paste disposal: Produced in conveyance and placement (either in WHAT WILL IT TAKE TO specialized paste thickeners, trucks or with conveyors/stackers) ADOPT ATD? or ultra-high-density thickeners and the unsaturated filtered tailings Mining is necessary for the technol- and transported by positive dis- may tend toward oxidation which ogy we use, vehicles we drive, “ATD placement pumps, the paste is can result in acid generation and medical devices that save lives, even generally used for backfill in drainage in acid generating tailings. that can of soda. However, tailings sounds like underground workings or in are the result of mining and how a win-win other situations where gravity IS ATD RIGHT FOR YOU? we handle tailings today may have opportunity, helps the flow. ATD sounds like a win-win opportu- a significant impact on the environ- Advantages: paste can be used nity, but it is not always easy. Each ment and communities in the very but it is not as backfill, reduced environmental mine is unique. The mine’s physical long term. We need to plan today always impact and disturbing less land, setting, the ore body, and the area’s to safely manage tailings long into absence of segregation, limited climate all greatly impact how the the future. easy” consolidation and associated seep- tailings can be handled. Considering Pair that future planning with age, no need for reclaim pond, as that the social setting is even more water scarcity and potential dam the material is partially saturated important, a tailings facility design safety concerns and the case for so no oxidization, higher in place has to be fit for purpose. While ATD gets even stronger. Although tailings density, therefore, lower recent failures have increased scru- capital costs for ATD alternatives embankment needed. tiny on the selection of conventional are typically higher than conven- Disadvantages: pumping materi- options, it remains important that tional, if future risk management and als of this consistency is not energy mine owners consider the issues at long-term liability reduction can be or cost efficient, so when the dis- each mine site and establish what quantified and considered in the posal site is some distance away would be best there. decision, the choice can be a lot from the mill it may be beneficial to There are many major considera- more attractive. If consideration of pump slurry with lower solids con- tions that limit ATD’s use: total cost (including closure and tent and have the water removal • Topography: Some technologies post-closure) is given greater weight operations close to the disposal site. lend themselves toward flat in the tailing disposal alternative topographies and sometimes are selection, ATD can start to become • Filtered tailings disposal: Tailing not even feasible at sites with ‘the norm’. materials are dewatered to 85% or moderately steep terrain. greater solids by weight ratio • Production rates: Operators seek THE NEXT STEPS using filers aided by a vacuum or reliable equipment and stable This is an exciting time to work confining pressure. The dewatered operations. Removing water using in the mining industry, especially tailing materials are transported filters or paste thickeners from in support of smart and safe tail- by conveyor or trucked to a dis- some tailings can be a challenge at ings management. Technology is posal area. high-production rates. Currently, changing the way we work. Stantec Advantages: reduced environ- conventional tailing disposal brings the whole toolbox with us mental risks, improved water conser- remains the default technology at when we come to a mine. We are vation, improved compliance, space high-production mines. experts in tailings design, alterna- conservation, better handling in cold • Climate: Although ATD methods tives assessments, operations condition and fewer topographic have been implemented in wet cli- support, closure and post-closure limitations. mates, their successful implemen- management. July/August 2021 www. .com.
Recommended publications
  • State of Utah DIVISION of WASTE MANAGEMENT GARY R
    Department of Environmental Quality L. Scott Baird Executive Director State of Utah DIVISION OF WASTE MANAGEMENT GARY R. HERBERT AND RADIATION CONTROL Governor Ty L. Howard SPENCER J. COX Director Lieutenant Governor November 5, 2020 Cassady Kristensen Environmental Business Partner Rio Tinto Kennecott 4700 Daybreak Parkway South Jordan, UT 84009 RE: Kennecott Utah Copper Tailings Impoundment Refuse Class IIIb Landfill Permit Dear Ms. Kristensen: The Division of Waste Management and Radiation Control (Division) has completed its review of the application to permit the Rio Tinto Kennecott Utah Copper Tailings Impoundment Refuse Class IIIb Landfill located on the Rio Tinto Kennecott Tailings Impoundment facility in Salt Lake County, Utah. Enclosed with this letter is the approved Permit Number 1905 and applicable attachments from portions of the application. The Permit approval and expiration dates are shown on the permit cover page. Also, the Statement of Basis for this permit (DSHW-2020-014707) is included with the permit. If you have any questions, please call Doug Taylor at (801) 536-0240. Sincerely, Ty L. Howard, Director Division of Waste Management and Radiation Control (Over) DSHW-2020-014711 195 North 1950 West • Salt Lake City, UT Mailing Address: P.O. Box 144880 • Salt Lake City, UT 84114-4880 Telephone (801) 536-0200 • Fax (801) 536-0222 • T.D.D. (801) 536-4284 www.deq.utah.gov Printed on 100% recycled paper TLH/DT/ar Enclosures: Permit (DSHW-2020-004084) Attachment #1 - Landfill Design (DSHW-2020-004510) Attachment #2 – Operation Plan (DSHW- 2020-004512) Attachment #3 – Closure and Post-Closure Plan (DSHW-2020-004514) Statement of Basis (DSHW-2020-014707) c: Gary Edwards, MS, Health Officer, Salt Lake County Health Dept.
    [Show full text]
  • Assessment of the Possible Reuse of Extractive Waste Coming from Abandoned Mine Sites: Case Study in Gorno, Italy
    sustainability Article Assessment of the Possible Reuse of Extractive Waste Coming from Abandoned Mine Sites: Case Study in Gorno, Italy Neha Mehta 1,2, Giovanna Antonella Dino 1,*, Iride Passarella 3, Franco Ajmone-Marsan 4, Piergiorgio Rossetti 1 and Domenico Antonio De Luca 1 1 Department of Earth Sciences, University of Turin, 10125 Torino, Italy; [email protected] (N.M.); [email protected] (P.R.); [email protected] (D.A.D.L.) 2 School of Mechanical and Aerospace Engineering, Queen’s University Belfast, Belfast, BT9 5AH, UK 3 Horizon s.r.l., 10095 Grugliasco (TO), Italy; [email protected] 4 Department of Agricultural, Forestry and Food Sciences, University of Turin, 10095 Grugliasco (TO), Italy; [email protected] * Correspondence: [email protected]; Tel.: +39-011-6705150 Received: 21 January 2020; Accepted: 17 March 2020; Published: 21 March 2020 Abstract: Supply of resources, a growing population, and environmental pollution are some of the main challenges facing the contemporary world. The rapid development of mining activities has produced huge amounts of waste. This waste, found in abandoned mine sites, provides the potential opportunity of extracting raw material. The current study, therefore, focuses on testing the validation of a shared methodology to recover extractive waste from abandoned mines, and applies this methodology to a case study in Gorno, northwest Italy. The methods focused on: (1) analyzing the impact of tailings and fine fraction of waste rock (<2 mm) on plants (Cress - Lepidium Sativum) to assess usability of both as soil additive, and (2) recovering raw materials from tailings and coarse fraction (>2 mm) of waste rock, by means of dressing methods like wet shaking table and froth flotation.
    [Show full text]
  • Environmental Lmpact Mine Development and Tailings Disposal
    .--L South Pocific Regionol Environm€nf Progromme ft -- Ittltt-'r'tl SPREP Reports ond Studies Series no, 95 WJ: Environmental lmPact Hffi Assessment Guidelines for Mine DeveloPment and ffi Tailings Disposal at Tropical Coastal Mines ar'' -il South Pocific Reglonol Environment Progromrre Environmental lmpact Assessment Guidelines for Mine Development and Tailings Disposal at Tropical Coastal Mines Prepared by Derek Ellls Assisted by Jacquellne Connolly SPREP Librry Cataloguing-in-Publication Dara Ellis,Dcsck Erwironmental impact ascsmcot guiddinca fq minc dcrrclopment 2ad t.ilingr dispod et topicel costal rnincs / grcprrcd \ p6d Ellir ard **itt"d bJ.cqudinc Connolly. - Apie,Vftstcrn Samoa : SPREB 1996. viii,26p. : 69., placcs, ublcs : 29 can- ISBN:982-04-0150-X 1. Environncntal impact rtetcmens.2. Mincs and rnincrrl rrsouroae - Erndrronmcnal aspccs, 3. Erwironmcnal monitori.g- I. C.onnolly, Jacquclinc. II. South Pacific Rcgiond Environmcnt Prognmmc. IV Tida 333.765 kcprrcd for putilication by thc South Pacifc Rcgionel Ernironmcot kogrlmmc, PO Bc 24o,Apb,Wcrtcrn Samoa @ South PacificRcgiorrl Environmcnt Plogrannc, 1996 Thc South Pecifc Rcgional En'ironncnt Plogrililnc authcbcs thc rcproduction of tcmud netcrid, wholc or parq in any form, providcd approprbtc acknorlcdgcmcot b gi\r€o. Original 3srt; F'ngfirh Editor Barbare Hcason Production Pctcr Erans Photographs Plare I (covcr and p.4) reproduced with permission of Island Copper Mine, BHP Minerals Canada Ltd; platc 6 (cover and p.6) and plate 5 reproduced with permission of Placcr Pacific Limited, Typeset in I l/13 Bembo and UR\7 Casde Printed on I l0gsm Tudor RP. (100% recyded) by ABC Printing, Brisbane, Australia Printed with finaocial assistance from AusAID Covcr photographs Top:The seale of uwu produaionfmm ninitg and milling prouses an be enotmorn, Hererun see the *uste mck dunry anil their redamation at klanil Coppa Mine, Canada.
    [Show full text]
  • Thesis, Dissertation
    AN EXPLORATION OF SMALL TOWN SENSIBILTIES by Lucas William Winter A thesis submitted in partial fulfillment of the requirements for the degree of Master of Architecture in Architecture MONTANA STATE UNIVERSITY Bozeman, Montana April 2010 ©COPYRIGHT by Lucas William Winter 2010 All Rights Reserved ii APPROVAL of a thesis submitted by Lucas William Winter This thesis has been read by each member of the thesis committee and has been found to be satisfactory regarding content, English usage, format, citation, bibliographic style, and consistency and is ready for submission to the Division of Graduate Education. Steven Juroszek Approved for the Department of Architecture Faith Rifki Approved for the Division of Graduate Education Dr. Carl A. Fox iii STATEMENT OF PERMISSION TO USE In presenting this thesis in partial fulfillment of the requirements for a master’s degree at Montana State University, I agree that the Library shall make it available to borrowers under rules of the Library. If I have indicated my intention to copyright this thesis by including a copyright notice page, copying is allowable only for scholarly purposes, consistent with “fair use” as prescribed in the U.S. Copyright Law. Requests for permission for extended quotation from or reproduction of this thesis in whole or in parts may be granted only by the copyright holder. Lucas William Winter April 2010 iv TABLE OF CONTENTS 1. THESIS STATEMENT AND INRO…...........................................................................1 2. HISTORY…....................................................................................................................4 3. INTERVIEW - WARREN AND ELIZABETH RONNING….....................................14 4. INTERVIEW - BOB BARTHELMESS.…………………...…....................................20 5. INTERVIEW - RUTH BROWN…………………………...…....................................27 6. INTERVIEW - VIRGINIA COFFEE …………………………...................................31 7. CRITICAL REGIONALISM AS RESPONSE TO GLOBALIZATION…………......38 8.
    [Show full text]
  • Litter Decomposition on Directly Revegetated Tailings at the Kidston Gold Mine, North Queensland, Australia1
    LITTER DECOMPOSITION ON DIRECTLY REVEGETATED TAILINGS AT THE KIDSTON GOLD MINE, NORTH QUEENSLAND, AUSTRALIA1 Andrew H. Grigg2 Abstract. An investigation of litter decomposition was undertaken at the Kidston Gold Mine in north Queensland, Australia with the aim of assessing the status of nutrient cycling capacity on a directly-revegetated tailings dam. Weight losses from leaf litter contained in litterbags placed in a 5-year old revegetated section of the dam were not significantly different from losses observed at two unmined reference sites over the 18 month study period, representing a rapid improvement in nutrient cycling capacity in the reconstructed ecosystem. However, fitted decay curves for each site predicted a slower decay constant and a longer litter half-life on the dam, which indicated that full pre-mining capability had not yet been achieved. Weight loss in the reconstructed system was most constrained by the low build-up of microbial biomass within the surface soil, which is expected to take at least 10 years to achieve pre-mining levels. In contrast, weight losses in the unmined sites appeared more related to the abundance of invertebrate fauna rather than microbial content. The results presented here of a developing system suggest that the importance of different factors affecting decomposition will reflect those that are most limiting over the course of ecosystem recovery. Additional Key Words: nutrient cycling, ecosystem recovery, microbial biomass, invertebrates. _____________________ 1Paper presented at the 2002 National Meeting of the American Society of Mining and Reclamation, Lexington KY, June 9-13, 2002. Published by ASMR, 3134 Montavesta Rd., Lexington, KY 40502.
    [Show full text]
  • Helpful Study Guide (PDF)
    WASTEWATER STABILIZATION POND (WWSP) STUDY GUIDE ALASKA DEPARTMENT OF ENVIRONMENTAL CONSERVATION DIVISION OF WATER OPERATOR TRAINING AND CERTIFICATION PROGRAM http://dec.alaska.gov/water/opcert/index.htm Phone: (907) 465-1139 Email: [email protected] January 2011 Edition Introduction This study guide is made available to examinees to prepare for the Wastewater Stabilization Pond (WWSP) certification exam. This study guide covers only topics concerning non-aerated WWSPs. The WWSP certification exam is comprised of 50 multiple choice questions in various topics. These topics will be addressed in this study guide. The procedure to apply for the WWSP certification exam is available on our website at: http://www.dec.state.ak.us/water/opcert/LargeSystem_Operator.htm. It is highly recommended that an examinee complete one of the following courses to prepare for the WWSP certification exam. 1. Montana Water Center Operator Basics 2005 Training Series, Wastewater Lagoon module; 2. ATTAC Lagoons online course; or 3. CSUS Operation of Wastewater Treatment Plants, Volume I, Wastewater Stabilization Pond chapter. If you have any questions, please contact the Operator Training and Certification Program staff at (907) 465-1139 or [email protected]. Definitions 1. Aerobic: A condition in which “free” or dissolved oxygen is present in an aquatic environment. 2. Algae: Simple microscopic plants that contain chlorophyll and require sunlight; they live suspended or floating in water, or attached to a surface such as a rock. 3. Anaerobic: A condition in which “free” or dissolved oxygen is not present in an aquatic environment. 4. Bacteria: Microscopic organisms consisting of a single living cell.
    [Show full text]
  • Safety Evaluation of the Zhaoli Tailings Dam a Seepage, Deformation and Stability Analysis with Geostudio
    UPTEC ES 16 031 Examensarbete 30 hp September 2016 Safety Evaluation of the Zhaoli Tailings Dam A seepage, deformation and stability analysis with GeoStudio Johan Bäckström Malin Ljungblad Abstract Safety Evaluation of the Zhaoli Tailings Dam Johan Bäckström and Malin Ljungblad Teknisk- naturvetenskaplig fakultet UTH-enheten The mining industry produce large amount of mine waste, also called tailings, which must be kept in tailings dams. In this thesis the safety and stability of a tailings dam Besöksadress: have been studied, where some of the tailing material is being used as filling material. Ångströmlaboratoriet Lägerhyddsvägen 1 The dam has been modelled and simulated using the software Geostudio. To evaluate Hus 4, Plan 0 the safety and stability of the dam seepage, stress and strain as well as slope stability have been simulated with SEEP/W, SIGMA/W and SLOPE/W, which are different Postadress: modules in the Geostudio software. Box 536 751 21 Uppsala The results show that the dam is stable for all tested scenarios. However, in this Telefon: thesis many simplifications and assumptions have been made so it is recommended to 018 – 471 30 03 do a more detailed study to confirm the safety of the dam. The dam should also be Telefax: simulated for earthquakes before a definite evaluation can be made. 018 – 471 30 00 This master thesis has been conducted in cooperation with Vattenfall AB, Energiforsk Hemsida: AB, Uppsala University and Tsinghua University in Beijing, China. The project has http://www.teknat.uu.se/student been carried out on the planned Zhaoli ditch tailing dam in the Shanxi Province, China.
    [Show full text]
  • Pond Infiltration and Watertable Mounding
    GEO-SLOPE International Ltd, Calgary, Alberta, Canada www.geo-slope.com Pond Infiltration and Watertable Mounding 1 Introduction The objective of this illustration is show how to model the filling of a pond with a liner. The zone below the liner remains unsaturated and the watertable deep in the profile mounds, due to percolation from the base of the pond. The modeling can help evaluate the effectiveness of lining the reservoir with a clay liner. Not only can the final, steady-state condition be established for both scenarios, but the rise in the watertable with time can be determined by conducting a transient analysis. Feature Highlights Transient boundary conditions Watertable viewing over time Unit flux boundary conditions Unsaturated flow 2 Geometry and boundary conditions The containment facility is located on top of a hill, with a stream at the bottom of the embankment, as shown below. Since the change in the regional system needs to be evaluated with time, a transient analysis will be conducted. 12 11 10 9 ) 8 m ( 7 n o i 6 t a v 5 e l E 4 3 2 1 0 0 2 4 6 8 10 12 14 16 18 20 22 24 26 28 30 Distance (m) Figure 1 Problem configuration Before conducting a transient analysis, it is sometimes helpful to know the long-term, steady-state solution, so you know the conditions where the system is eventually going to stabilize. It can also be helpful as a point of reference to compare against your transient results, which can help you determine if the steady-state solution is reasonable or too far in the future to be considered obtainable.
    [Show full text]
  • Introduction to Ponds, Lagoons, and Natural Systems Study Guide December 2013 Edition
    Wisconsin Department of Natural Resources Wastewater Operator Certification Introduction to Ponds, Lagoons, and Natural Systems Study Guide December 2013 Edition Subclass D Wisconsin Department of Natural Resources Bureau of Science Services, Operator Certification Program PO Box 7921, Madison, WI 53707 http://dnr.wi.gov/ The Wisconsin Department of Natural Resources provides equal opportunity in its employment, programs, services, and functions under an Affirmative Action Plan. If you have any questions, please write to Equal Opportunity Office, Department of Interior, Washington, D.C. 20240. This publication is available in alternative format (large print, Braille, audio tape. etc.) upon request. Please call (608) 266-0531 for more information. Printed on 12/06/13 Introduction to Ponds, Lagoons, and Natural Systems Study Guide - December 2013 Edition Preface This operator's study guide represents the results of an ambitious program. Operators of wastewater facilities, regulators, educators and local officials, jointly prepared the objectives and exam questions for this subclass. How to use this study guide with references In preparation for the exams you should: 1. Read all of the key knowledges for each objective. 2. Use the resources listed at the end of the study guide for additional information. 3. Review all key knowledges until you fully understand them and know them by memory. It is advisable that the operator take classroom or online training in this process before attempting the certification exam. Choosing a Test Date: Before you choose a test date, consider the training opportunities available in your area. A listing of training opportunities and exam dates is available on the internet at http://dnr.wi.gov, keyword search "operator certification".
    [Show full text]
  • Evaporation Pond Seepage Soil Solution
    from the soil surface. The subcores were fitted and sealed with plexiglass ends and set up to measure Permeability. Drainage water having an electrical conductivity (EC) of 10 dS/m (6100 ppm total dissolved salts) was applied to the cores for three days to ensure saturation and uniform electrolyte concentration. Biological activity was minimized in some of the cores by the addition of chlo- roform to the percolating drain water. Percolating drainage water having pro- gressively larger EC values was applied over periods of one to five days in an effort to exaggerate variations in evaporation pond salinity resulting from evaporation lnfiltrometers (left)were installed in Kings County and fresh drain water additions. The sa- evaporation pond to estimate seepage. Rainfall, evaporation, drainage flows, and changes in pond linity of inflow and outflow water was water levels (herebeing checked by co-author Blake measured periodically along with the per- McCullough-Sanden)were also measured. meability of each subcore. The sodium adsorption ratio (SAR) is an index of the relative concentration of sodium, calcium, and magnesium in the Evaporation pond seepage soil solution. When soil salinity is low, permeability has been shown to increase Mark E. Grismer o Blake L. McCullough-Sanden as the SAR value of the inflow solution in- creases. Past studies, however, have typi- cally considered SAR values of 30 or less. Rates of seepage from operating evaporation In this study, SAR values of the inflow so- ponds decline substantially as they age and as lution increased in the same stepwise fashion as EC, with values ranging from salinity increases 210 to 660.
    [Show full text]
  • Tailings Pond Rehabilitation Project and Effluent Management System Upgrade, Baldivis
    Tailings pond rehabilitation project and effluent management system upgrade, Baldivis Western Mining Corporation Ltd Report and recommendation of the Environmental Protection Authority Environmental Protection Authority Bulletin 489 January 1991 Taiiings pond rehabiiitation project and effluent management system upgrade, Baldivis Western Mining Corporation Ltd Report and recommendation of the Environmentai Protection Authority ISBN 0 7309 3593 0 ISSN 1030 0120 Assessment Number 323 Contents Page Summary and recommendation 1. Background 1 2. The proposal 1 2.1 The tailings pond 2.2 Timing 3 3. Potential environmental impacts assessed by the Environmental Protection Authority 3 3.1 Lake Cooloongup 3 3.2 Terrestrial vegetation 3 4~ Conclusion 5 Figures 1 ~Tailings pond locality plan 2 2. Proposed timing of activities described in CER 4 Appendices 1 List of Commitments made by the Proponent 2. Proponent's response to issues raised during the assessment process 3. Llst of organisations and members of the public that made submissions Summary and recommendation In 1969, Western Mining Corporation Limited (WMC's) constructed a tailings pond in Baldivis, 7 km from the Company's Kwinana Nickel Refinery, to store solid and liquid wastes from the refinery. In March 1979, it was discovered that the tailings pond was leaking ammonium sulphate solution to the ground1..vater resulting in contamination of tr1e bottom ·third of the groundv;ater body (aquifer). it is not c!ear whether any subsequent environmental impacts have occurred and none has been properly identified at this time. However, this absence of obvious environmental impact could be attributed to the depth of the contamination within the aquifer and that it is overlain by a significant thickness of good quality groundwater.
    [Show full text]
  • Management of Sulfide-Bearing Waste, a Challenge for the Mining Industry
    Minerals 2012, 2, 1-10; doi:10.3390/min2010001 OPEN ACCESS minerals ISSN 2075-163X www.mdpi.com/journal/minerals/ Review Management of Sulfide-Bearing Waste, a Challenge for the Mining Industry Björn Öhlander 1,*, Terrence Chatwin 2 and Lena Alakangas 1 1 Department of Geosciences, Luleå University of Technology, SE-971 87 Luleå, Sweden; E-Mail: [email protected] 2 International Network for Acid Prevention, 2105 Oneida Street, Salt Lake City, UT 84109, USA; E-Mail: [email protected] * Author to whom correspondence should be addressed; E-Mail: [email protected]; Tel.: +46-920-491396; Fax: +46-920-491199. Received: 13 December 2011; in revised form: 3 January 2012 / Accepted: 2 February 2012 / Published: 8 February 2012 Abstract: Oxidation of iron sulfides in waste rock dumps and tailings deposits may result in formation of acid rock drainage (ARD), which often is a challenging problem at mine sites. Therefore, integrating an ARD management plan into the actual mine operations in the early phases of exploration, continuing through the mine life until final closure might be successful and decrease the environmental impact. A thorough characterization of ore and waste should be performed at an early stage. A detailed knowledge of mineralogical composition, chemical composition and physical properties such as grain size, porosity and hydraulic conductivity of the different waste types is necessary for reliable predictions of ARD formation and efficiency of mitigation measures. Different approaches to prevent and mitigate ARD are discussed. Another key element of successfully planning to prevent ARD and to close a mining operation sustainably is to engage the mine stakeholders (regulators, community and government leaders, non-governmental organization (NGOs) and lenders) in helping develop and implement the ARD management plan.
    [Show full text]