Auswahl der wissenschaftlichen Literatur zum Thema „The disposal of mine waste“

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Zeitschriftenartikel zum Thema "The disposal of mine waste"

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GASKIN, P. „Disposal of Mine Waste.“ International Journal of the Society of Materials Engineering for Resources 4, Nr. 1 (1996): 41–47. http://dx.doi.org/10.5188/ijsmer.4.41.

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Oldecop, Luciano, und Germán Rodari. „Unsaturated mine tailings disposal“. Soils and Rocks 44, Nr. 3 (13.08.2021): 1–12. http://dx.doi.org/10.28927/sr.2021.067421.

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Filtered tailings is the disposal technology that is most likely to yield an unsaturated state of the tailings. Such state has important benefits. A dam to contain the mine wastes is no longer needed, the risk of polluting seepage is minimized, and liquefaction of tailings is prevented. Filtering also allows most of the water mixed with the tailings to be recovered and reused in the process. The resulting material can be handled with traditional soil moving equipment to form a stack, for instance. While the idea is simple, the multiple phenomena involved in the tailings unsaturated disposal make up a complex process. The present work is based on a case study, the Casposo Mine filtered tailings disposal facility, located in the central Andes of Argentina. Throughout ten years of operation, a series of field and laboratory studies have been carried out to characterize the phenomena that intervene in the disposal of filtered tailings. Two stages were studied in detail: air drying upon tailings discharge and tailings compression under the weight of the subsequent lifts of the stack. Flocculant agents were found to have an outstanding influence in the tailings behaviour. Because of the multiple influencing factors, the process outcome (namely, the tailings water content and their void ratio) is highly variable. To deal with such variability, projects must include enough redundancy. In this regard, the case study’s incorporation of waste rock layers interspersed between tailings layers was a successful experience.
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Lapakko, K. A. „Subaqueous Disposal of Mine Waste: Laboratory Investigation“. Journal American Society of Mining and Reclamation 1994, Nr. 1 (1994): 270–78. http://dx.doi.org/10.21000/jasmr94010270.

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WIEDEMANN, H. „Report: Deep mine disposal of hazardous waste“. Waste Management & Research 9, Nr. 1 (Februar 1991): 65–66. http://dx.doi.org/10.1016/0734-242x(91)90088-o.

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Wickland, Benjamin E., G. Ward Wilson, Dharma Wijewickreme und Bern Klein. „Design and evaluation of mixtures of mine waste rock and tailings“. Canadian Geotechnical Journal 43, Nr. 9 (01.09.2006): 928–45. http://dx.doi.org/10.1139/t06-058.

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The technique of mixing mine waste rock and tailings for disposal has the potential to avoid the problems of acid rock drainage and tailings liquefaction. This paper presents a rational basis for the design of mixtures based on particle packing theory and laboratory investigations. Mixtures were conceptualized using a particle model that allows mixture design and interpretation of behaviour. Laboratory investigations included examination of tailings rheology, mixture trials, and compressibility testing of waste rock, tailings, and mixtures of waste rock and tailings. Results indicate that mixture design governs mixture structure, and consequently also compressibility behaviour. A method is presented to predict mixture compressibility from mixture ratio and the properties of the parent waste rock and tailings. The study provides theory for the design and evaluation of mixtures as a mine waste disposal technique and demonstrates that the design of geotechnical properties is possible for homogeneous mixtures of mine wastes at the laboratory scale.Key words: co-disposal, particle packing, rheology, compressibility, waste rock, tailings.
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Brierley, Corale L. „Mine waste management“. Waste Management 13, Nr. 4 (Januar 1993): 359–60. http://dx.doi.org/10.1016/0956-053x(93)90068-8.

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Brunskill, Gregg. „Mine Waste Disposal in the Ocean: An Introduction“. Oceanography 25, Nr. 2 (01.06.2012): 166–69. http://dx.doi.org/10.5670/oceanog.2012.52.

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Kutepov, Yuriy, Aleksandr Mironov, Maksim Sablin und Elena Borger. „Substantiation of Safe Conditions During Undermining of Hydraulic Waste Disposal“. E3S Web of Conferences 41 (2018): 01007. http://dx.doi.org/10.1051/e3sconf/20184101007.

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This article considers mining and geological conditions of the site “Blagodatny” of the mine named after A.D. Ruban located underneaththe old open pit coal mine and the hydraulic-mine dump. The potentially dangerous zones in the undermined rock mass have been identified based onthe conditions of formation of water inflow into mine workings. Safe depthof coal seams mining has been calculated depending on the type of water body – the hydraulic-mine dump.
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Huang, Wen Zhang, und Ning Lu. „Study on Procedure Toxicity and Harmless Disposal of Manganese Mine Tailing Slag“. Advanced Materials Research 414 (Dezember 2011): 312–16. http://dx.doi.org/10.4028/www.scientific.net/amr.414.312.

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Manganese mine slag was the salvage in the course of manganese producing. Many matters shall be extracted by rain eluviation and then turn into the water and soil to pollute environment. The water content and extraction procedure toxicity of the manganese waste residue were studied. Combining solidification additive was used to process the manganese waste residue for the harmless disposal. The results showed that the contents of Manganese、Zinc、Chromium and Cadmium in the manganese waste slag exceeded the maximum of the Chinese Identification standard for hazardous wastes. The extraction procedure toxicity was effectively decreased by the harmless disposal when the proportion of cement and manganese in the whole mine slag was 60%, and the content of heavy metals in the leaching solution were under the standard. Hence, the method of cement solidification could control the pollution to the environment effectively.
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Wickland, Benjamin E., und G. Ward Wilson. „Self-weight consolidation of mixtures of mine waste rock and tailings“. Canadian Geotechnical Journal 42, Nr. 2 (01.04.2005): 327–39. http://dx.doi.org/10.1139/t04-108.

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Mixtures of waste rock and tailings are compared with unmixed waste rock and tailings in a column study of self weight consolidation. Standard practice for surface mine waste disposal produces the two individual waste streams of waste rock and tailings. Waste rock dumps offer high strength and low compressibility characteristics but are prone to oxidation and metal leaching because of their high permeability and unsaturated conditions. Tailings deposits typically have low permeability and slow time rate consolidation properties but also have end land use issues and long term stability problems related to shear strength. Three mixtures of waste rock and tailings were loaded into columns and monitored for settlement, drainage, and pore-water pressure response for 100 days. A fourth column was built with waste rock only as a control. Mixtures with approximately 5:1 waste rock to tailings by dry mass were found to have a hydraulic conductivity similar to tailings alone and total settlements similar to waste rock alone. Mixture materials also remained saturated during the 100 day test. Results indicate that mixing waste rock and tailings for disposal is a promising idea that may help eliminate problems arising from current practices in mine waste disposal.Key words: co-disposal, hydraulic conductivity, self weight consolidation, tailings, waste rock.
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Dissertationen zum Thema "The disposal of mine waste"

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Gosling, Christine. „Co-disposal of rejects from coal and sand mining operations in the Blue Mountains : a feasibility study /“. View thesis, 1999. http://library.uws.edu.au/adt-NUWS/public/adt-NUWS20030822.133548/index.html.

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Cotter-Howells, Jane. „Lead minerals in soils contaminated by mine-waste : implications for human health“. Thesis, Imperial College London, 1991. http://hdl.handle.net/10044/1/8913.

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Bamber, Andrew Sherliker. „Integrated mining, pre-concentration and waste disposal systems for the increased sustainability of hard rock metal mining“. Thesis, University of British Columbia, 2008. http://hdl.handle.net/2429/779.

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The integration of automated ore pre-concentration and waste disposal functions into the hard rock metal mining system, prior to treatment by conventional grinding and flotation, is proposed as a novel interpretation of Mine-Mill Integration for improving the economics and environmental impact of exploiting deep, low-grade or otherwise marginal mineral deposits. The proposed approach seeks to reject coarse, barren waste from the ore stream as early as possible in the mining cycle, and safely dispose of it as backfill underground. The concept is proposed as a Lean Manufacturing approach to hard rock mining, as an alternative to improving the economics of mining simply by increasing the mining rate. Lean Manufacturing philosophy seeks to design out overburden, smooth production, and eliminate waste from the system. It is suggested that the introduction of these systems into the hard rock mining process addresses all three of these areas of Lean thinking, and is thus an important approach to be considered for surface or underground mines wishing to simultaneously improve efficiency, economics and environmental performance, thus increasing the life, and the sustainability of the operation. The application of integrated mining, processing and waste disposal systems, where appropriate, is proposed as a strategy for the development of efficient new mining operations, or alternately the expansion of production at existing mines. Technologies specific to the success of the approach such as automated ore pre-concentration systems, composite fill preparation and delivery systems, as well as continuous mechanized mining methods are explored. The impacts and benefits of applying these integrated technologies to the mining system are defined and quantified through research, testwork, engineering design and systems analysis. Custom geo-metallurgical evaluation tools incorporating mineralogical, metallurgical, geophysical and geotechnical methods have been developed to allow the assessment of ores in terms of their potential for the adoption of the proposed approach. A computerized parametric evaluation model has also been developed to quantify the potential impacts and benefits using data from this testwork. A wide range of case studies have been investigated with positive results, and important conclusions are drawn towards the potential for application of the concept as a generalized case.
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Mitchell, Paul Brian. „The application of industrial minerals in the control of pollution emanating from metalliferous mine waste“. Thesis, University of Exeter, 1991. http://ethos.bl.uk/OrderDetails.do?uin=uk.bl.ethos.293379.

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Waller, Caroline P. „Dispersion of heavy metals and arsenic from mine waste into adjacent farmland in west Cornwall“. Thesis, University of Exeter, 1995. http://ethos.bl.uk/OrderDetails.do?uin=uk.bl.ethos.318183.

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Lee, Matthew R. „The effects of the disposal of copper mine tailings on littoral meiofaunal assemblages of the Chanaral area of northern Chile“. Thesis, Bangor University, 2001. http://ethos.bl.uk/OrderDetails.do?uin=uk.bl.ethos.367316.

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Gosling, Christine, University of Western Sydney und School of Civic Engineering and Environment. „Co-disposal of rejects from coal and sand mining operations in the Blue Mountains : a feasibility study“. THESIS_XXXX_CEE_Gosling_C.xml, 1999. http://handle.uws.edu.au:8081/1959.7/824.

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This thesis presents details of investigations into the potential for co-disposal of the two rejects from Clarence Colliery and Kable's Transport Sand Mine. Column experiments were undertaken to simulate field conditions. The experiment consisted of: 1/. creating the required co-disposal arrangement and structure in containers 2/. infiltrating water through each container and measuring the rates of infiltration and overflow 3/. measuring the chemical properties of the leachate water. Geotechnical tests of co-disposal pile stability were undertaken using a specially constructed shear box. Results of this study suggest the co-disposal of course coal washery reject from Clarence Colliery with clay tailings from Kable's Transport Sand Mine is a feasible option for managing the generation of acetic drainage. It is recommended that field trials comprise layers of coal reject and clay tailings in a 9:1 ratio. Layering the coal reject with clay tailings creates a semi-permeable barrier which acts to restrict water percolation through the reject as well as reacting with the leachate to increase the leachate pH and adsorb metals
Master of Engineering (Hons)
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Chikusa, Chimwemwe Mainsfield. „Pollution caused by mine dumps and its control“. Thesis, Rhodes University, 1994. http://hdl.handle.net/10962/d1005603.

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All mine dumps are a point source of either physical, chemical or both forms of pollution. Physical pollution includes the physical site coverage of the dump, slumping of parts of the dams and dust that may originate from it (air pollution). Chemical pollution from, or related to the mine dumps include the dominant acid drainage (which contains heavy metals), radioactivity, electromagnetic radiation, noise and chemicals released from the mineral processing stage. In one way or the other, exposure to these pollution forms is detrimental to the human health and his environment. It is this fact that urges the public, government and the responsible mining companies to find ways of monitoring the pollution and stopping it, preferably at the source. Where it can not be stopped, techniques of reducing it, or containing it have been, and are still being developed. Personal protection is the priority. Pollution exposure to the general public is minimised as much as possible. Pollution control techniques that employ less expensive, natural, self-sustaining elements suitable for the environment such as wetlands and vegetation are recommended. The artificial short term and often expensive alternatives are of secondary priority. However, choice of which technique to use is based on the merit of each problem, knowing that chemicals act faster but are effective for a short period as compared to the natural systems. Pollution management is the critical part of the whole process. This involves decision making on courses of action and financial allocation on the part of both the polluter and the monitoring department/agent. The ability to effectively manage pollution programmes is achieved these days with the aid of computers. It is emphasised that pollution control should be handled in an integrated, multi-disciplinary approach manner. This is because pollution is a question of life and death, hence every individual remains accountable to it. Keeping the public and the concerned parties educated, informed and welcoming their concerns on the environmental issues related to the mine dumps generated in a mining venture is essential in the modern days of environmental public awareness, or otherwise face the public lath.
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Rammika, Modise. „An ion imprinted polymer for the determination of Ni (II) ions from mine tailing samples“. Thesis, Rhodes University, 2011. http://hdl.handle.net/10962/d1004981.

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A Ni(II)-dimethylglyoxime ion imprinted polymer {Ni(II)-DMG IIP} was synthesized by the trapping method using the bulk polymerisation format. The structures of the imprinted and non-imprinted polymer were evaluated by infrared spectroscopy and the morphology was observed by scanning electron microscopy. The Ni(II)-DMG IIP was optimised for pH, mass, time and by the uniform design experimental method for the molar ratios of monomer to crosslinker to porogen and template to ligands as well as keeping these parameters constant and varying the quantities of initiator, 2,2'-azobisisobutyronitrile (AIBN). The optimum pH was 8.5, optimum mass was 50 mg, optimum time was 1 min and the optimum molar ratios of crosslinker to monomer, monomer to template and nickel(II) sulfate hexahydrate (NiSO₄.6H₂O) to 4-vinylpyridine to dimethylglyoxime were found to be 3.3:1.0, 0.6:1.0 and 1.0:0.6:3.6 respectively with 30 mg and 8 mL as the optimum amounts of initiator and porogen respectively. Through this optimisation, recovery of Ni(II) was increased from 98 to 100%. Selectivity of the ion imprinted polymer was evaluated by analysing, using an inductively coupled plasma-optical emission spectrometer, for Ni(II) ions that were spiked with varying concentrations of Co(II), Cu(II), Zn(II), Pd(II), Fe(II), Ca(II), Mg(II), Na(I) and K(I) in aqueous samples. Selectivity studies also confirmed that the ion imprinted polymer had very good selectivity characterised by % RSD of less than 5 %. Co(II) was the only ion found to slightly interfere with the determination of Ni(II). The limits of detection and quantification were found to be 3x10⁻⁴ μg/mL and 9x10⁻⁴ μg/mL respectively. The method was evaluated by a custom solution of ground water certified reference material (SEP-3) and sandy soil reference material (BCR-142R) and the concentrations of Ni(II) obtained were not significantly different to the certified ones. The Ni(II)-DMG IIP was then evaluated in aqueous and soil samples where recoveries of 93 to 100% and 98 to 99% respectively were obtained with enrichment factors ranging from 2 to 18 in aqueous and 27 to 40 in soil samples. Finally, the Ni(II)-DMG IIP was used to analyse mine tailings samples and Ni(II) recovery of 99% was obtained with an enrichment factor of 2.
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Albuquerque, Allwyn J. J. „Geoenvironmental aspects of coal refuse-fly ash blends /“. This resource online, 1994. http://scholar.lib.vt.edu/theses/available/etd-12042009-020142/.

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Bücher zum Thema "The disposal of mine waste"

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Boldt, C. M. K. Beach characteristics of mine waste tailings. Pgh. [i.e. Pittsburgh] Pa: U.S. Dept. of the Interior, Bureau of Mines, 1988.

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Boldt, C. M. K. Beach characteristics of mine waste tailings. Pgh. [i.e. Pittsburgh] Pa: U.S. Department of the Interior, Bureau of Mines, 1988.

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Blight, G. E. Geotechnical engineering for mine waste storage facilities. Boca Raton: CRC Press, 2010.

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Blight, G. E. Geotechnical engineering for mine waste storage facilities. Boca Raton: CRC Press, 2010.

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Geotechnical engineering for mine waste storage facilities. Boca Raton: CRC Press, 2010.

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Ltd, Rescan Environmental Services. Subaqueous disposal of reactive mine wastes: An overview. Ottawa, Ont: Canada Centre for Mineral and Energy Technology = Centre canadien de la technologie des minéraux et de l'énergie, 1989.

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Chan, W. K. Geotechnical aspects of waste disposal at Suncor oil sands mine. S.l: s.n, 1989.

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International Mine Water Association African Symposium on Mine Drainage and Environment Protection from Mine Waste Water Disposal (1st 1993 Konkola Division, Chililabombwe, Zambia). International Mine Water Association First African Symposium on Mine Drainage and Environment Protection from Mine Waste Water Disposal. Chililabombwe, Zambia: The Association, 1993.

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Robertson, Kevin. Characterization of nickel hydroxide sludge using the variable pressure SEM. Montréal, Qué: Dept.of Mining, Metals and Materials Engineering, McGill University, 2004.

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Ltd, Rescan Environmental Services. Geochemical assessment of subaqueous tailings disposal in Buttle Lake, British Columbia. Ottawa, Ont: Canada Centre for Mineral and Energy Technology = Centre canadien de la technologie des minéraux et de l'énergie, 1990.

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Buchteile zum Thema "The disposal of mine waste"

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Van Zyl, Dirk. „Mine waste disposal“. In Geotechnical Practice for Waste Disposal, 269–86. Boston, MA: Springer US, 1993. http://dx.doi.org/10.1007/978-1-4615-3070-1_12.

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Wu, Di. „Solutions for Surface Disposal of Mine Tailings“. In Mine Waste Management in China: Recent Development, 11–19. Singapore: Springer Singapore, 2019. http://dx.doi.org/10.1007/978-981-32-9216-1_2.

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Antonaki, Nonika, Tarek Abdoun und Inthuorn Sasanakul. „Centrifuge Modeling of Mine Tailings and Waste Rock Co-disposal, Consolidation and Dynamic Loading“. In Sustainable Civil Infrastructures, 25–34. Cham: Springer International Publishing, 2017. http://dx.doi.org/10.1007/978-3-319-63543-9_3.

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Jakovljević, Ksenija, Dragana Ranđelović und Tomica Mišljenović. „Phytoremediation of Mine Waste Disposal Sites: Current State of Knowledge and Examples of Good Practice“. In Biotechnology for Sustainable Environment, 223–50. Singapore: Springer Singapore, 2021. http://dx.doi.org/10.1007/978-981-16-1955-7_9.

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Paria, Christ Jesus Barriga, Hernani Mota de Lima und Eleonardo Lucas Pereira. „Optimization of Disposal Areas by Studying of the Mining Rock Waste Granulometry of an Iron Mine“. In Proceedings of the 8th International Congress on Environmental Geotechnics Volume 3, 242–52. Singapore: Springer Singapore, 2018. http://dx.doi.org/10.1007/978-981-13-2227-3_30.

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Marriott, Norman G., und Gill Robertson. „Waste Disposal“. In Food Science Texts Series, 114–28. Boston, MA: Springer US, 1997. http://dx.doi.org/10.1007/978-1-4615-6045-6_8.

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Bilitewski, Bernd, Georg Härdtle und Klaus Marek. „Waste Disposal“. In Waste Management, 259–338. Berlin, Heidelberg: Springer Berlin Heidelberg, 1997. http://dx.doi.org/10.1007/978-3-662-03382-1_5.

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Ennow, Klaus. „Waste Disposal“. In Safety and Efficacy of Radiopharmaceuticals 1987, 249–59. Dordrecht: Springer Netherlands, 1987. http://dx.doi.org/10.1007/978-94-009-3375-0_18.

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Chandrappa, Ramesha, und Diganta Bhusan Das. „Disposal“. In Solid Waste Management, 117–46. Berlin, Heidelberg: Springer Berlin Heidelberg, 2012. http://dx.doi.org/10.1007/978-3-642-28681-0_5.

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Jagger, John. „Nuclear Waste Disposal“. In The Nuclear Lion, 133–57. Boston, MA: Springer US, 1991. http://dx.doi.org/10.1007/978-1-4899-2784-2_10.

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Konferenzberichte zum Thema "The disposal of mine waste"

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Schultze, Martin, Bertram Boehrer, Kurt Friese, Matthias Koschorreck, Sebastian Stasik und Katrin Wendt-Potthoff. „Disposal of waste materials at the bottom of pit lakes“. In Sixth International Conference on Mine Closure. Australian Centre for Geomechanics, Perth, 2011. http://dx.doi.org/10.36487/acg_rep/1152_58_schultze.

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Steel, Abigail, Kelly Hawboldt und Faisal Khan. „An integrated, risk-based approach for design of mine waste long-term disposal facilities“. In Sixth International Conference on Mine Closure. Australian Centre for Geomechanics, Perth, 2011. http://dx.doi.org/10.36487/acg_rep/1152_106_steel.

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Creek, Mike, Matthew Wickham und Gordan Gjerapic. „Evapotranspiration cover performance in a high desert environment, north waste rock disposal facility, Rain Mine, USA“. In Sixth International Conference on Mine Closure. Australian Centre for Geomechanics, Perth, 2011. http://dx.doi.org/10.36487/acg_rep/1152_33_creek.

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Muldoon, Joe, und Laurier L. Schramm. „Gunnar Uranium Mine Environmental Remediation: Northern Saskatchewan“. In ASME 2009 12th International Conference on Environmental Remediation and Radioactive Waste Management. ASMEDC, 2009. http://dx.doi.org/10.1115/icem2009-16102.

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Thirty-six now-abandoned uranium mine and mill sites were developed and operated in Northern Saskatchewan, Canada, from approximately 1957 through 1964. During their operating lifetimes these mines produced large quantities of ore and tailings. The Gunnar Mine is located on the shores of Lake Athabasca, the 22nd largest lake in the world. The Gunnar mine (open pit and underground) produced over 5 million tonnes of uranium ore and nearly 4.4 million tonnes of mine tailings. There is an estimated 2,710,700 m3 of waste rock that abuts the shores of Lake Athabasca. After closure in the 1960’s, the Gunnar site along with all of the other uranium mine and mill sites were abandoned with little remediation and no reclamation being done. The governments of Canada and Saskatchewan are now funding the clean-up of these abandoned northern uranium mine and mill sites and have contracted the management of the project to the Saskatchewan Research Council. The clean-up activity is expected to take about 8 years, followed by 10–15 years of monitoring activity before the sites are to be released into an institutional controls program that will allow government oversight of a long term management and monitoring program. The Gunnar site, because of the magnitude of tailings and waste rock, is subject to an environmental site assessment process regulated by both provincial and federal governments. This process requires a detailed study of the projected environmental impacts resulting from the mining activities and an analysis of projected impacts from remediation efforts. Prescribed environmental and land use endpoints will be made based on the environmental assessment studies and remediation options analyzed and implemented based on expected results. Remediation options range from deep lake disposal of tailings to disposal of tailings in the open pit which is now filled with water and fish (contaminated, but which are reproducing successfully) to covering the tailings with a cap. The site also includes many buildings that are remnants of a community of approximately 800 people who once occupied the site. These buildings, many of which contain asbestos, must be appropriately removed and disposed of. The original mine head frame and mill site buildings, many of which still contain the original machinery and equipment, must also be removed and disposed of. The regulatory requirements include the environmental assessment processes, a complex public involvement strategy and licensing from the Canadian Nuclear Safety Commission. The environmental assessment process, specific site studies and public involvement initiatives are underway with the long term goal of releasing the property in a fully remediated state.
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Hobbs, Steve. „Assessing and managing the long-term risks and liabilities at a closed Cornish mine used for waste disposal“. In Eighth International Seminar on Mine Closure. Australian Centre for Geomechanics, Cornwall, 2013. http://dx.doi.org/10.36487/acg_rep/1352_43_hobbs.

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Kristiansen, Håvard, und Bernt Sigve Aadnøy. „Borehole Disposal of Nuclear Waste“. In SPE/IADC International Drilling Conference and Exhibition. SPE, 2021. http://dx.doi.org/10.2118/204117-ms.

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Abstract Approximately 370 000 tons of high-level radioactive waste exists. Some nations have mature projects for disposing of such waste in mined repositories hundreds of meters below ground. Emplacement in boreholes of greater depth could be a cost-efficient and fast alternative, particularly for nations with relatively small amounts of waste. A borehole repository could be developed via an iterative process, which would ultimately end with the completion of a comprehensive safety case and a fully operational disposal facility which would be sealed and decommissioned in a reliable manner. Each design should be adapted to the properties of the waste in question, site-specific geological conditions, and regulatory requirements. This variability causes designs and cost estimates to differ. Overall, borehole disposal of high-level radioactive waste is an opportunity for the drilling industry to expand its service portfolio in a way that is beneficial to the environment and the safety of current and future generations.
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7

Wu, Ai-xiang, Hua-zhe Jiao, Hong-jiang Wang und Sheng-kai Yang. „Notice of Retraction: Paste Filling - A Underground Disposal Technique of Mine Solid Waste“. In 2011 5th International Conference on Bioinformatics and Biomedical Engineering. IEEE, 2011. http://dx.doi.org/10.1109/icbbe.2011.5781452.

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8

Antonaki, Nonika, Tarek Abdoun und Inthuorn Sasanakul. „Centrifuge Modeling of Mine Tailings and Waste Rock Co-Disposal, Consolidation, and Dynamic Loading“. In Geo-Chicago 2016. Reston, VA: American Society of Civil Engineers, 2016. http://dx.doi.org/10.1061/9780784480137.025.

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9

Watson, Andrew, Patrick Corser, E. Garces Pardo, T. Lopez Christian und Jos Vandekeybus. „A comparison of alternative tailings disposal methods — the promises and realities“. In First International Seminar on the Reduction of Risk in the Management of Tailings and Mine Waste. Australian Centre for Geomechanics, Perth, 2010. http://dx.doi.org/10.36487/acg_rep/1008_41_watson.

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10

Ghose, Shankar. „Engineered Barriers in the Waste Isolation Pilot Plant“. In 10th International Conference on Nuclear Engineering. ASMEDC, 2002. http://dx.doi.org/10.1115/icone10-22087.

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The Waste Isolation Pilot Plant (WIPP) is a deep geological repository being developed by the Department of Energy as a research and disposal facility in the bedded salt deposit of New Mexico. WIPP is essentially an underground salt mine at 2150 feet (655 meters) below the surface and operates on multiple barrier mechanism. Engineered barriers provide an additional protective measure to prevent the movement of fluid towards the accessible environment. Four types of engineered barriers are used in the WIPP disposal system. This paper presents an analysis of the effectiveness of the engineered barriers in various repository environments.
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Berichte der Organisationen zum Thema "The disposal of mine waste"

1

Henghu Sun und Yuan Yao. Research and Development of a New Silica-Alumina Based Cementitious Material Largely Using Coal Refuse for Mine Backfill, Mine Sealing and Waste Disposal Stabilization. Office of Scientific and Technical Information (OSTI), Juni 2012. http://dx.doi.org/10.2172/1048945.

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2

Skone, Timothy J. Storage/Disposal Coal Mine Tailings. Office of Scientific and Technical Information (OSTI), Juni 2014. http://dx.doi.org/10.2172/1509136.

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3

Tolan, T. L. The use of protective barriers to deter inadvertent human intrusion into a mined geologic facility for the disposal of radioactive waste: A review of previous investigations and potential concepts. Office of Scientific and Technical Information (OSTI), Juni 1993. http://dx.doi.org/10.2172/10183215.

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4

Grygiel, M. L., C. A. Augustine, M. A. Cahill, J. S. Garfield, M. E. Johnson, M. J. Kupfer, G. A. Meyer et al. Tank Waste Disposal Program redefinition. Office of Scientific and Technical Information (OSTI), Oktober 1991. http://dx.doi.org/10.2172/10108555.

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5

Van Hoesen, S. (Low-level radioactive waste disposal). Office of Scientific and Technical Information (OSTI), Juni 1985. http://dx.doi.org/10.2172/5273682.

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6

CSA ENGINEERING INC MOUNTAIN VIEW CA. Safe Disposal of Secondary Waste. Fort Belvoir, VA: Defense Technical Information Center, April 2007. http://dx.doi.org/10.21236/ada476421.

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7

Hamm, L. L., F. G. III Smith, G. P. Flach, R. A. Hiergesell und B. T. Butcher. Unreviewed Disposal Question Evaluation: Waste Disposal In Engineered Trench #3. Office of Scientific and Technical Information (OSTI), Juli 2013. http://dx.doi.org/10.2172/1089500.

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8

Unknown. DISPOSAL OF FLUIDIZED BED COMBUSTION ASH IN AN UNDERGROUND MINE TO CONTROL ACID MINE DRAINAGE AND SUBSIDENCE. Office of Scientific and Technical Information (OSTI), April 1999. http://dx.doi.org/10.2172/783694.

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9

Unknown. DISPOSAL OF FLUIDIZED BED COMBUSTION ASH IN AN UNDERGROUND MINE TO CONTROL ACID MINE DRAINAGE AND SUBSIDENCE. Office of Scientific and Technical Information (OSTI), Juli 1999. http://dx.doi.org/10.2172/783695.

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Unknown. DISPOSAL OF FLUIDIZED BED COMBUSTION ASH IN AN UNDERGROUND MINE TO CONTROL ACID MINE DRAINAGE AND SUBSIDENCE. Office of Scientific and Technical Information (OSTI), Januar 2000. http://dx.doi.org/10.2172/783696.

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