Wet Barriers on Pyritic Uranium Tailings

Total Page:16

File Type:pdf, Size:1020Kb

Wet Barriers on Pyritic Uranium Tailings Wet Barriers on Pyrite Uranium Tailings Laboratory Lysimeter Studiesof Oxidation, Leaching and Limestone Neutralization Characteristics of Uranium Tailings and Waste Rock MEND Project 2.13.la Part 1: - Oxidation and LeachingCharacteristics of Total Mill Tailings, CoarseTailings and Waste Rock, and Limestone Neutralization Characteristicsof Tailings mixed with Limestone,under Unsaturatedand Batch Leaching Conditions Part II: - Oxidation and Lcaching Characteristicsof CoarseTailings under SubmergedConditions This work was done on behalf of MEND and sponsored by the Canada Centre for Minera1 and Energy Technology (CANMET) and Rio Algom Limited Elliot Lake, Ontario January1998 Wet Barriers on Pyritic Uranium Tailings Part I and II Laboratory Lysimeter Studies of Oxidation, Leaching and Limestone Neutralization Characteristics of Uranium Tailings and Waste Rock Nand K. Davé Report MMSL 98 - 001 (CR) January 1998 Part I: - Oxidation and Leaching Characteristics of Total Mill Tailings, Coarse Tailings and Waste Rock, and Limestone Neutralization Characteristics of Tailings mixed with Limestone, under Unsaturated and Batch Leaching Conditions Part II: - Oxidation and Leaching Characteristics of Coarse Tailings under Submerged Conditions Work Performed for Rio Algom Limited, Elliot Lake, Ontario under Contract No. 50948 i WET BARRIERS ON PYRITIC URANIUM TAILINGS PART I AND II LABORATORY LYSIMETER STUDIES OF OXIDATION, LEACHING AND LIMESTONE NEUTRALIZATION CHARACTERISTICS OF URANIUM TAILINGS AND WASTE ROCK Nand K. Davé* EXECUTIVE SUMMARY This report describes the results of laboratory column leaching studies that were conducted as a part of a broad research program titled “Development of Wet Barriers on Pyritic Uranium Tailings for Controlling Acid Generation”. The research was undertaken jointly by CANMET, Elliot Lake Laboratory and Rio Algom Limited, under the Canadian Mine Environmental Neutral Drainage (MEND) Program. Purpose: Column leaching studies were conducted for evaluating the oxidation and leaching characteristics of pyritic uranium tailings with and without limestone amendments and crushed waste rock, under unsaturated and submerged conditions. These experiments were designed to determine the acid generation characteristics and subsequent metal and radionuclide releases of test samples subjected to submersion underwater and exposed conditions. Methods: The leaching experiments were conducted using PVC cylindrical column lysimeters filled with total mill tailings, coarse tailings, tailings amended with 7.5% (w/w) limestone of varying screen *Senior Environmental Research Scientist, Elliot Lake Laboratory, CANMET, Natural Resources, Canada. ii sizes, and crushed waste rock samples obtained from Quirke Mine. The experiments provided unsaturated conditions for leaching of test samples as well as a submerged condition for coarse tailings where a shallow water cover, 0.45 m in depth, was established using distilled water. The submerged coarse tailings were also rinsed rapidly during the initial leaching period to remove gypsum and other soluble minerals for studying oxidation and leaching characteristics of such tailings in the absence of gypsum controlled sulphate solubility. All tests were conducted at laboratory room temperature (22 ºC) and light conditions, which aided in enhancing the chemical reactivity of test materials in laboratory simulations compared to field conditions. Duration of the Study: The experiments, conducted at the CANMET, Elliot Lake Laboratory, were started in April 1989 and concluded in June 1993. Results: Coarse Tailings: Unsaturated Condition: · The unsaturated coarse tailings without limestone amendment oxidized readily and produced highly acidic drainage (pH ~ 1.0 - 2.0 and acidity ~ 12,000 - 30,000 mg CaCO3/l); · The coarse tailings amended with coarse limestone (screen size -6.3 mm) also produced highly acidic drainage (pH ~ 2.5 - 3.0 and acidity ~ 4,000 - 12,000 mg CaCO3/l), but its onset was delayed by approximately one year in comparison to coarse tailings without limestone. The acid drainage occurred with 90% of the available alkalinity still remaining in the sample; iii · The coarse tailings amended with pulverized wet ground limestone did not produce any acidic drainage during the entire four year study period. Oxidation and acid generation processes were active in these tailings as well, but the fine grained limestone provided complete acid neutralization and acidic drainage was prevented during the study period. Submerged Condition: · The submerged coarse tailings did not produce any porewater acidic drainage for the first three years, but in the fourth year a weak acidic drainage (pH ~ 5.5 - 7.0 and acidity ~ 10 -20 mg CaCO3/l) was observed ; · In comparison to unsaturated coarse tailings, submersion of tailings underwater decreased cumulative porewater acidity, sulphate and iron loadings by factors of 295, 200 and 950 respectively; · The submersion of coarse tailings also resulted in increased mobility and release of Ra-226 in the porewater when tailings developed acidic conditions at the surface after they were depleted of available alkalinity and gypsum. There was a 10 fold increase in the cumulative loading of Ra-226 in the porewater over that of unsaturated coarse tailings; · The increased drainage of Ra-226 in the porewater was also accompanied by that of iron, both occurring near the end of the fourth year, where as gypsum was completely removed from the tailings during the first three months of leaching; · The surface water above submerged tailings contained low concentrations of dissolved metals, when the water cover above the tailings was continuously maintained in a well oxygenated condition by fresh water inflow and where both surface and pore water flows were present in equal proportions. The dissolved Ra-226 concentration in the surface water was also low, ranging between 30 and 140 mBq/l. iv Total Mill Tailings: Unsaturated Condition: · The total mill tailings, in all test conditions, drained poorly and retained appreciable amounts of moisture which controlled their oxidation and acid generation rates; · The unsaturated total mill tailings without limestone amendment also produced acid drainage, but it was moderate and less acidic (pH ~ 2.0 - 3.0 and acidity ~ 500 - 1500 mg CaCO3/l) than for coarse tailings under similar conditions; · The total mill tailings amended with various screen-sized limestone did not produce acid drainages during the entire study period. The tailings were oxidizing slowly but the added limestone was actively consumed in providing complete acid neutralization in all amended samples. Waste Rock: Unsaturated Conditions: · The unsaturated crushed waste rock having a high acid generation potential (NNP = -17.8 kg CaCO3/tonne) also oxidized and started to produce highly acidic drainage ( pH ~ 2.0 - 2.5 and acidity ~ 7,000 - 20,000 mg CaCO3/l) in the fourth year of the study period; · The unsaturated crushed waste rock having medium (NNP = -10.7 kg CaCO3/tonne) and low (NNP = +13.8 kg CaCO3/tonne) acid generation potentials did not produce acidic drainage during the entire study period. v DETAILED SUMMARY OF FINDINGS In 1989, under the Mine Environmental Neutral Drainage (MEND) program, a joint research project titled “Development of Wet Barriers on Pyritic Uranium Tailings for Controlling Acid Generation” was established between CANMET, Elliot Lake Laboratory and Rio Algom Limited, Elliot Lake, Ontario, Canada. This research program encompassed a variety of laboratory and field studies designed to evaluate the performance of a shallow water cover or other wet barriers on pyritic uranium tailings as a close-out option for controlling acid generation and release of metals and radionuclides. As a part of this program, extensive laboratory column leaching studies were conducted to evaluate oxidation and leaching characteristics of tailings and waste rock samples under unsaturated conditions, tailings amended with 7.5 % (w/w) limestone of varying screen sizes, and submerged coarse tailings. For these tests, two types of tailings and three types of waste rock were chosen. The two types of tailings were: total mill tailings (unclassified), approximately 50 % less than 74 mm; and coarse tailings, approximately 84 % greater than 74 mm. The three types of waste rock were categorized as having, low (NNP = +13.8), medium (NNP = -10.7) and high (NNP = -17.8 kg CaCO3/tonne) acid generation potentials. The experiments were conducted in PVC columns, under unsaturated and submerged conditions. T he latter tests were conducted only for coarse tailings, where a shallow water cover, approximately 0.45 m in depth, was provided using distilled water. For both unsaturated and submerged cases, the tailings or waste rock were allowed to weather at the exposed surface or tailing / water interface and leached with natural lake or distilled water (for submerged tailings only). The unsaturated tailings and waste rock were batch leached by adding 1 l (litre) natural lake water every two weeks where as the submerged tailings were trickle leached with a continuous inflow of distilled water. The leachates were allowed to vi percolate through the test media and collected as drainage effluents from the bottom of the columns in all cases. The experiments, conducted at the CANMET, Elliot Lake Laboratory, were started in April 1989 and concluded in June 1993. Table S1 provides a brief summary of various test conditions and porewater drainage (seepage) quality results for this laboratory
Recommended publications
  • CMD 18-M48.9A File/Dossier : 6.02.04 Date
    CMD 18-M48.9A File/dossier : 6.02.04 Date : 2018-12-03 Edocs pdf : 5725730 Revised written submission from Mémoire révisé de Northwatch Northwatch In the Matter of À l’égard de Regulatory Oversight Report for Uranium Rapport de surveillance réglementaire des Mines, Mills, Historic and Decommissioned mines et usines de concentration d’uranium et Sites in Canada: 2017 des sites historiques et déclassés au Canada : 2017 Commission Meeting Réunion de la Commission December 12, 2018 Le 12 décembre 2018 Revised version with changes made on pages 5 and 6 November 20, 2018 Canadian Nuclear Safety Commission 280 Slater Street, P.O. Box 1046, Station B Ottawa, ON K1P 5S9 Ref. CMD 18-M48 Dear President Velshi and Commission Members: Re. Regulatory Oversight Report for Uranium Mines, Mills, Historic and Decommissioned Sites in Canada: 2017 On 29 June 2018 the Secretariat for the Canadian Nuclear Safety Commission provided notice that the Commission would hold a public meeting in December 2018 during which CNSC staff will present its Regulatory Oversight Report for Uranium Mines, Mills, Historic and Decommissioned Sites in Canada: 2017. The notice further indicated that the Report would be available after October 12, 2018, online or by request to the Secretariat, and that members of the public who have an interest or expertise on this matter are invited to comment, in writing, on the Report by November 13 2017. Northwatch provides these comments further to that Notice. Northwatch appreciates the extension of the deadline for submission of our comments by one week in response to delays in finalizing the contribution agreement which had to be in place prior to our technical experts beginning their review.
    [Show full text]
  • Ontario Mine Rescue Competition Awards
    Ontario Mine Rescue Competition Awards JUNE 2018 Table of Contents Provincial Championship Award (M.S.A. Trophy) John Guthrie (Special Equipment) Award Firefighting Award First Aid Award Equipment Technician Award Kirkland Lake District Onaping District Red Lake District Southern District Sudbury District Thunder Bay/Algoma District Timmins District Former District Trophies Provincial Championship Award The M.S.A. Trophy, donated by MSA Canada Ltd., has been awarded to the top team in the annual Provincial Mine Rescue Competition since 1955. A cut and polished granitoid slab with plaque rests above a silver, trapezoidal engraved scene of a linked six-man mine rescue team wearing McCaa breathing apparatus. The team is traversing a double-tracked drift, as the lead rescuer holds a Wolf flame safety lamp, while the second holds a self-rescuer. The trophy originally consisted only of the slab and the first tier with the engraving. The bottom three tiers were added. 1950 – Pamour Porcupine Gold Mines 1987 – Denison Mines Ltd. 1951 – Hallnor Mines Ltd. 1988 – Denison Mines Ltd. 1952 – Hollinger Consolidated Gold Mines Ltd. 1989 – American Barrick Resources 1953 – Falconbridge Nickel Mines Ltd. - Holt McDermott Mine 1954 – MacLeod Cockshutt Gold Mines Ltd. 1990 – Sifto Canada, Goderich Mine 1955 – Kerr Addison Gold Mines Ltd. 1991 – Placer Dome Inc., Campbell Mine 1956 – Falconbridge Nickel Mines Ltd. 1992 – Placer Dome Inc., Dome Mine - East Mine 1993 – Inco Ltd., Frood Stobie Complex 1957 – Steep Rock Iron Mines Ltd. 1994 – Inco Ltd., Levack Complex 1958 – Steep Rock Iron Mines Ltd. 1995 – Inco Ltd., Frood Stobie Complex 1959 – Algom Uranium Mines Ltd. 1996 – Falconbridge, Onaping Craig Mine - Quirke Mine 1997 – Falconbridge 1960 – Falconbridge Nickel Mines Ltd.
    [Show full text]
  • RADIONUCLIDE UPTAKE by BEAVER and RUFFED GROUSE in the SERPENT RIVER BASIN by F.V
    E^ffiiSH^ SMS wmmmm ca9110891 RADIONUCLIDE UPTAKE BY BEAVER AND RUFFED GROUSE IN THE SERPENT RIVER BASIN by F.V. Clulow Laurentian University .^S^t^^^i^R «m *IMis Atomic Energy Commission de controle 1*1 Control Board de lenergie atomique INFO-0292 PO Box 1046 CP 1046 Onawa. Canada Ottawa Canada K1P5S9 K1P5S9 RADIONUCLIDE UPTAKE BY BEAVER AND RUFFED GROUSE IN THE SERPENT RIVER BASIN by F.V. Clulov, Laurentian University A research report prepared for the Atomic Energy Control Board Ottawa, Canada December 1988 Canada Research report RADIONUCLIDE UPTAKE BY BEAYER AND RUFFED GROUSE IN THE SERPENT RIVER BASIN / A report presented to the Atomic Energy Control Board by F. Clulow, Laurentian University. ABSTRACT Radionuclide levels were measured in tissues, gut contents, and diet items of adult beaver and ruffed grouse from the Serpent River drainage basin (which contains the city of Elliot Lake) and control sites in Ontario, and in beaver and muskrat fetuses frcm females taken in the same basin. Levels of radium 226 in beaver bone, muscle and kidney were highest in animals from locations close to uranium tailings; liver levels did not vary by site. Grouse taken near Elliot Lake has higher bone levels of radium 226 than distant controls; levels in other tissues did not vary by site. Environmental radi-Tn 226 levels were within ranges previously reported at these or similar locations elsewhere; levels in beaver and grouse gut contents reflected levels in diet items. Fetal beaver tissues had higher radium 226 levels than maternal tissues; fetal liver tissue carried higher levels than other body tissues in general; fetal levels varied with maternal levels but also inversely with fetal size (and thus age).
    [Show full text]
  • APPENDIX A: MINERAL PROJECT 1. Property Description And
    APPENDIX A: MINERAL PROJECT 1. Property Description and Location (a) The Appia uranium-REE property (the “Property”) comprises a group of 100 unpatented staked mineral claims located in Buckles, Bouck, Beange, Bolger, Gunterman, Joubin and Lehman Townships and near the town of Elliot Lake in north-central Ontario. Elliot Lake is located on Highway 108 approximately 26 km north of Highway 17, also known as the Trans-Canada Highway. The area is situated in UTM zone 17. The geographic co-ordinates of the town of Elliot Lake are 46o23’N latitude and 82o39’W longitude. The Property totals 12,545 hectares (31,000 acres) encompassing five mineralized zones called Teasdale, Banana Lake, Canuc, Bouck Lake and Buckles Lake. The claims have not been surveyed. (b) Appia has a 100% interest in the mineral rights, having initially acquired 61 claims from Canada Enerco Corporation (“CEC”), a related company, under the terms of an agreement dated November 1, 2007. CEC originally staked the claims in accordance with the Mining Act of Ontario. Two claims were transferred to Denison Mines Inc. (“Denison”) in order to permit the construction of a new tailings infrastructure; in exchange Appia acquired the right of access onto claims held by Denison in the Elliot Lake area as well as the right to use former Denison mine workings to facilitate the exploration and development by Appia. Denison granted Appia a 3% net smelter return royalty on any production from the two claims transferred by Appia. Appia purchased 6 claims from Dan Patrie Exploration Ltd. (“Patrie”) in February 2008 and subsequently staked an additional 35 claims.
    [Show full text]
  • The Regulatory Control of Radioactive Waste Management
    Cov-Regul Control RWM NEA3597 16/02/04 11:10 Page 1 Radioactive Waste Management The Regulatory Control of Radioactive Waste Management Overview of 15 NEA Member Countries NUCLEAR•ENERGY•AGENCY Radioactive Waste Management The Regulatory Control of Radioactive Waste Management Overview of 15 NEA Member Countries © OECD 2004 NEA No. 3597 NUCLEAR ENERGY AGENCY ORGANISATION FOR ECONOMIC CO-OPERATION AND DEVELOPMENT ORGANISATION FOR ECONOMIC CO-OPERATION AND DEVELOPMENT Pursuant to Article 1 of the Convention signed in Paris on 14th December 1960, and which came into force on 30th September 1961, the Organisation for Economic Co-operation and Development (OECD) shall promote policies designed: − to achieve the highest sustainable economic growth and employment and a rising standard of living in member countries, while maintaining financial stability, and thus to contribute to the development of the world economy; − to contribute to sound economic expansion in member as well as non-member countries in the process of economic development; and − to contribute to the expansion of world trade on a multilateral, non-discriminatory basis in accordance with international obligations. The original member countries of the OECD are Austria, Belgium, Canada, Denmark, France, Germany, Greece, Iceland, Ireland, Italy, Luxembourg, the Netherlands, Norway, Portugal, Spain, Sweden, Switzerland, Turkey, the United Kingdom and the United States. The following countries became members subsequently through accession at the dates indicated hereafter: Japan (28th April 1964), Finland (28th January 1969), Australia (7th June 1971), New Zealand (29th May 1973), Mexico (18th May 1994), the Czech Republic (21st December 1995), Hungary (7th May 1996), Poland (22nd November 1996), Korea (12th December 1996) and the Slovak Republic (14 December 2000).
    [Show full text]
  • Uranium and Thorium Deposits of Northern Ontario
    Ontario Geological Survey Mineral Deposits Circular 25 Uranium and Thorium Deposits of Northern Ontario by James A. Robertson and Kerry L. Gould This project was partially funded by the Ministry of Northern Affairs 1983 Ministry of Hoa Alan w. Pope Minister Natural lA(__ , W. T. Foster Resources Deputy Minister Ontario Copyright OMNR 1983 ISSN 0706-4551 Printed in Canada ISBN 0-7743-8439-5 Publications of the Ontario Ministry of Natural Resources are available from the following sources. Orders for publications should be accompanied by cheque or money order payable to the Treasurer of Ontario. Reports, maps, and price lists (personal shopping or mail order): Public Service Centre, Ministry of Natural Resources Room 1640, Whitney Block, Queen's Park Toronto, Ontario M7A 1W3 Reports and accompanying maps only (personal shopping). Ontario Government Bookstore Main Floor, 880 Bay Street Toronto, Ontario Reports and accompanying maps (mail order or telephone orders): Publications Services Section, Ministry of Government Services 5th Floor, 880 Bay Street Toronto, Ontario M7A 1N8 Telephone (local calls), 965-6015 Toll-free long distance, 1-800-268-7540 Toll-free from area code 807, O-ZENITH-67200 Every possible effort is made to ensure the accuracy of the information contained in this report, but the Ministry of Natural Resources does not assume any liability for errors that may occur. Source references are included in the report and users may wish to verify critical information. Parts of this publication may be quoted if credit is given. It is recommended that reference to this report be made in the following form: Robertson, J.A., and Gould, K.L 1983: Uranium and Thorium Deposits of Northern Ontario; Ontario Geological Survey, Mineral Deposits Circular 25, 152p.
    [Show full text]
  • The Blind River Uranium Deposits: the Ores and Their Setting
    Ontario Division of Mines THE BLIND RIVER URANIUM DEPOSITS: THE ORES AND THEIR SETTING by James A. Robertson MISCELLANEOUS PAPER 65 1976 MINISTRY OF NATURAL RESOURCES Ontario Division of Mines HONOURABLE LEO BERNIER, Minister of Natural Resources DR. J. K. REYNOLDS, Deputy Minister of Natural Resources G. A. Jewett, Executive Director, Division of Mines E. G. Pye, Director, Geological Branch THE BLIND RIVER URANIUM DEPOSITS: THE ORES AND THEIR SETTING1 by James A.Robertson MISCELLANEOUS PAPER 65 1976 MINISTRY OF NATURAL RESOURCES 1A paper presented at a workshop sponsored by the United States Geoloqical Survey on The Genesis of Uranium—and Gold-Bearing Precambrian Quartz- Pebble Conglomerates at Golden, Colorado, October 13 to 14, 1975. ©ODM 1976 Publications of the Ontario Division of Mines and price list are obtainable through the Ontario Ministry of Natural Resources, Map Unit, Public Service Centre Queen's Park, Toronto, Ontario and The Ontario Government Bookstore 880 Bay Street, Toronto, Ontario. Orders for publications should be accompanied by cheque, or money order, payable to Treasurer of Ontario. Parts of this publication may be quoted if credit is given to the Ontario Division of Mines. It is recommended that reference to this report be made in the following form- Robertson, James, A. 1976: The Blind River Uranium Deposits: The Ores and Their Setting; Ontario Div. Mines, MP 65, 45p. 3000-300-1976-BP CONTENTS PAGE Abstract ;• Introduction I Regional Geology 1 Table of Formations 2-3 Archean (Early Precambrian) ."> Keewatin-Type
    [Show full text]
  • Performance of Shallow Water Covers on Pyritic Uranium Tailings
    Performance of Shallow Water Covers on Pyritic Uranium Tailings I Ludgate1, A Coggan2 and N K Davé3 ABSTRACT The ore was hosted as metamorphosed quartz-pebble conglomerate with the mineralisation confined mainly to the The performance of in situ, shallow water covers in controlling acid generation was evaluated at four recently decommissioned pyritic cementing material that bound the pebbles. The uranium milling uranium tailings sites at Elliot Lake, Ontario, Canada. The tailings are and extraction processes consisted of hot-sulfuric-acid leaching, acid generating, having a pyrite content of approximately five to ten per using compressed air or hydrogen peroxide as an oxidant, cent and a very low to non-existent alkaline buffering capacity. followed by ion-exchange separation and precipitation as Adverse market conditions led to the closure of all operating uranium ammonium di-uranate or magnesium uranate (yellow cake). The mines in the early- to mid-1990s, followed by rehabilitation and latter process was adopted for newer second-generation mills for decommissioning of mine and waste management facilities. In order to decreasing the total ammonia load to the environment. control acidic drainage, all new and active tailings areas at Denison, The tailings were neutralised and deposited in surface-based Quirke, Panel, Spanish-American and Stanleigh mine sites were overland tailings impoundments. The Tailings Management re-engineered to provide in situ submersion of these tailings under Areas (TMAs) were generally located in valley depressions shallow water covers. The tailings impoundment dams were upgraded and reinforced or in some cases reconstructed, to minimise seepages and bounded by upland ridges and outcrops and impounded by provide a minimum 1 m depth of water cover.
    [Show full text]
  • Current Expansion of Th Ellio
    IN[S-mf _- CURRENT EXPANSION OF TH ELLIO BY: 6. STENNING, P. ENG. 'IANAGER OF ENGINEERING SERVICES OENISON MINES LIMITED ELLIOT LAKE, ONTARIO PRESENTED TO: 22N0 AMNUAL INTERNATIONAL CONFERENCE CANADIAN NtiaEAR ASSOCIATION TORONTO, ONTARIO TUESDAY 8 JUNE Î982 J ABSTRACT The Elliot Lake mines are located in Northern Ontario, on the north shore of Lake Huron and along the edge of the Quirke syncline, covering . an area of some thirty square miles. Mining operations in this area were started in the mid-1950's and were severely restricted during the 1960's. Starting in 1973, Rio Algom's Quirke Mine and Denison, the only mines remaining in operation, started to make plans to expand. It was planned to increase production from a total of 13,400 tpd (milled) to approximately 30,000 tpd (milled), which required the re-opening of the Panel and Stanleigh Mines of the Rio Algom group, and the Stanrock-CanMet area at Denison. The first phase of the expansion was preceded by extensive public hearings before an Environmental Assessment Board. Hearings lasted approxi- mately 30 months, and covered every aspect of environmental conditions, assessment of community needs, a review of current and proposed mining methods, current mill process operations and alternatives and a thorough analysis of tailings disposal plans with discussion of long term strategies. Presentations were made by the mining companies, federal and provincial agencies, special Interest groups, and the public at large. More specifically, the expansion required an increase of production at the Rio Algom Quirke Mine from 4,500 to 7,000 tpd (milled), and the dewatering and re-opening of the Panel mine and mill for production at a rate of 3,300 tpd, with an alternate process in the mill operation.
    [Show full text]
  • Uranium Mining in Canada – Past and Present
    Uranium Mining in Canada – Past and Present Background notes for a presentation to the Indigenous World Uranium Summit November 30-December 1, 2006 Window Rock, Arizona Jamie Kneen, MiningWatch Canada Historic Mines – underground mines, tailings unconfined at older mines (dumped on land and/or in lakes) and in dry or underwater dams (natural lakes or valleys) at newer mines (1950s and later):1 . Port Radium (Eldorado mine), Northwest Territories o Pitchblende was discovered at Great Bear Lake in the Northwest Territories in 1930. In 1943, in order to gain control of all sources of uranium in their respective countries, the governments of Canada, the United Kingdom and the United States banned all private exploration for, and development of, radioactive materials. The federal government established a Crown corporation, Eldorado Mining and Refining Limited, to oversee Canadian uranium interests. This company expropriated the uranium mine at Port Radium and was given a monopoly in all uranium prospecting and developing activities.2 The Port Radium site was decommissioned in 1984. Clean-up and reclamation work recently undertaken. Rayrock mine, Northwest Territories o Staked in 1948; development underway by Rayrock Mines Limited in 1955. Production commenced in 1957 and ceased due to lack of economic reserves in 1959. A small townsite built by the company was in operation during this period. The mine employed 135 men in 1958 and the townsite had 20 families as residents. The Rayrock site was abandoned in 1959.3 Indian and Northern Affairs Canada began the decommissioning and rehabilitation of the Rayrock site including capping of the tailings in 1996.
    [Show full text]
  • Written Submission from Northwatch Mémoire De Northwatch
    CMD 18-M48.9 File/dossier : 6.02.04 Date : 2018-11-20 Edocs pdf : 5715702 Written submission from Mémoire de Northwatch Northwatch In the Matter of À l’égard de Regulatory Oversight Report for Uranium Rapport de surveillance réglementaire des Mines, Mills, Historic and Decommissioned mines et usines de concentration d’uranium et Sites in Canada: 2017 des sites historiques et déclassés au Canada : 2017 Commission Meeting Réunion de la Commission December 12, 2018 Le 12 décembre 2018 November 20, 2018 Canadian Nuclear Safety Commission 280 Slater Street, P.O. Box 1046, Station B Ottawa, ON K1P 5S9 Ref. CMD 18-M48 Dear President Velshi and Commission Members: Re. Regulatory Oversight Report for Uranium Mines, Mills, Historic and Decommissioned Sites in Canada: 2017 On 29 June 2018 the Secretariat for the Canadian Nuclear Safety Commission provided notice that the Commission would hold a public meeting in December 2018 during which CNSC staff will present its Regulatory Oversight Report for Uranium Mines, Mills, Historic and Decommissioned Sites in Canada: 2017. The notice further indicated that the Report would be available after October 12, 2018, online or by request to the Secretariat, and that members of the public who have an interest or expertise on this matter are invited to comment, in writing, on the Report by November 13 2017. Northwatch provides these comments further to that Notice. Northwatch appreciates the extension of the deadline for submission of our comments by one week in response to delays in finalizing the contribution agreement which had to be in place prior to our technical experts beginning their review.
    [Show full text]
  • Elliot Lake, Ontario Uranium Mines a Legacy Perpetual Care Case Study
    Mine Closure 2019 - AB Fourie & M Tibbett (eds) © 2019 Australian Centre for Geomechanics, Perth, ISBN 978-0-9876389-3-9 doi:10.36487/ACG_rep/1915_92_Berthelot Elliot Lake, Ontario uranium mines a legacy perpetual care case study DS Berthelot BHP, Canada D Place-Hoskie BHP, USA D Willems BHP, USA K Black BHP, USA Abstract Twelve uranium mines were opened in the vicinity of Elliot Lake, Ontario Canada between 1955 and 1958. In the early 1960s, eight of these mines were acquired and amalgamated to form Rio Algom Limited (RAL), now a subsidiary of BHP. During the 1960s only two mines were operational with remaining mines placed in care and maintenance. Two mines were reactivated and one expanded in the late 1970s and subsequently closed between 1990 and 1996. This construction and operating history produced eight tailings management areas with 102 Mt of tailings (range of 0.08 to 46 Mt), covering 920 ha (range of 13 ha to 400 ha) and various cover configurations (water, vegetated and combinations thereof). As part of the federal environmental assessment review process for closure, all facilities were subject to cost-benefit analysis to select final closure configuration. Closure was implemented at all facilities between 1992 and 2000 to meet then best practice for nuclear waste facilities. This paper will provide a 20-year post-closure perspective of water management, water treatment and watershed performance and key learnings for these perpetual care facilities. Keywords: closure, perpetual care, legacy sites, water management, water treatment 1 Introduction Twelve underground uranium mines and eleven mills were opened in the vicinity of Elliot Lake, Ontario Canada between 1955 and 1958 (Figure 1).
    [Show full text]