Thesis is submitted in partial fulfilment for the degree of Master of Science in Metallurgical Engineering to the Faculty of Engineering and the Built Environment, at the University of the Witwatersrand, Johannesburg, 2017 / Abandoned mines in South Africa have created a series of environmental legacies around the mining community in the form of health hazard (air pollution), land degradation and illegal mining activities. The biggest mine environmental legacy that is being addressed today in South Africa is that of abandoned mines, particularly asbestos and the process of cleaning up asbestos mining dumps in South Africa as implemented by Mintek (state owned mineral processing and metallaurgical research instistute)on behalf of Department of Mineral Resources (DMR) and this form the main basis of this research study. The history of abandoned mines, particularly asbestos mining, is that the mining peaked and took place during the time when there were no environmental regulations forcing mining companies to take control of their waste. The only legislation was the Atmospheric Pollution Prevention Act (Act No.45 of 1965). The Mineral Act, which regulated most of the mining activity in South Africa was promulgated in 1991 and was enacted as Act No.50 in 1991. Apart from the environmental challenges, these mines are located in rural areas with high unemployment levels and poor infrastructure, and therefore all solutions would require these matter to be addressed as well. This study was based on a literature review involving bamboo as a potential vegetation cover to be grown on abandoned mineland both for rehabilitation and with intention to harvest it for energy use. This would hope to address some of the socioeconomic issues within the communities surrounding such abandoned asbestos mines. Penge area in the Limpopo Province is proposed as the site for a pilot study for such bamboo cultivation. Bamboos are a large group of rapidly growing woody grasses, mainly found in the IndoChina regions of the world that can be sustainably managed in short-cycle harvesting schemes. They offer many benefits like erosion control, architectural properties for rural construction activities and can be used as biomass feedstock for the bioenergy economy. The results of this study indicate that it is possible to grow bamboo in the Penge based on its physio-climatic conditions. The literature review proposes , Bambusa balcooa, Dendrocalamus asper, Dendrocalamus strictus and Phyllostachys edulis as suitable bamboo species for the region. Based on rudimetary simple evaluation model the area will produce 14 tonnes/ha/year of biomass in the 5th year of harvesting, increasing to and stabilizing to 47 tonnes /ha/year in the 7th year and it has proven economically feasible to proudce energy from the amount of feedstock generated. / XL2018

Thesis (M.S.)--West Virginia University, 2009. / Title from document title page. Document formatted into pages; contains xvii, 195 p. : ill. (some col.), col. map. Includes abstract. Includes bibliographical references (p. 58-90).

Thesis (M.S.)--Ohio University, November, 2009. / Title from PDF t.p. Includes bibliographical references.

Mine reclamation is a long-term process but few long-term (> 15 years) assessment studies are carried out. Considerable effort has gone into test-plot experiments to design revegetation programs prior to termination of mine production but little is known from the results of this work of the long-term effect of competitive interactions between seeded species themselves and between seeded and immigrating native species during the progression to a natural vegetation for that site. The present study revisited and repeated benchmark scientific studies carried out at five mine-sites during the period 1973-1978. The mine-sites were Bull River mine, Coal Creek mine, Cumberland No. 4 mine, Pinchi Lake mine and Texada Iron mines. They were in different biogeoclimatic locations and at each mine, sample sites were located on different waste materials. On-site studies carried out during the 1993 field season included substrate observation and sampling, and visual observation of plant species and percent cover. Substrate samples were later analysed in the laboratory for soil nutrients. The graphical presentation of data honours the original data and is an effective way of assessing the development of substrate health and plant succession. Results show that if sufficient attention is paid to improving land-form then over a long period natural regenerative processes can accomplish remarkable results. Moisture deficiency will restrict growth to deep rooting, drought tolerant species and result in slow encroachment. This may require intensive management if erosion is likely. This type of study performed by staff with interdisciplinary training or experience can be used to make economical long-term assessments of site rehabilitation. They would not in any way replace the detailed quantitative monitoring conducted at critical phases early in the decommissioning process. However, as a complement, such studies could provide data for predicting long-term development on newer sites. In addition, they are an ecologically acceptable alternative to assessments of "productivity" on sites where rehabilitation is slow.

Public involvement in decisions about mine reclamation presents challenges to government, industry and the public. Among them are inclusion of relevant interests, representation, dealing with ignorance and misconceptions, uncertain science and technology, conflicting values, and very long spans of time. Planning theory suggests there is no preferred method, "no ideal solution to the conflict among the legitimate demand for public participation, the need for technical and economic rationality, and the necessity of assuring accountability and responsibility of decision making bodies" (Renn et al., 1993). In the 1990s, public involvement was introduced into reclamation planning and decision making processes at three metal mines in British Columbia: Brenda, Sullivan and Island Copper. A review of them shows that different techniques have been used. At Brenda a public surveillance committee was formed to review and comment on reclamation options produced by the mine in co-operation with a technical committee comprised of regulatory officials. At Sullivan a single committee consisting of public representatives, mine staff and regulatory officials met to review a draft reclamation plan and recommend amendments. At Island Copper a round table was convened to examine the use of the site as a regional landfill. Based on unpublished primary documents (mainly minutes), supplemented by published material and informal interviews, the public involvement processes were first classified and then evaluated. Criteria for the classification and evaluation were drawn from planning literature. The classification focused on purpose and methods. Public involvement mainly functioned at a consultative or advisory level. Of the three processes reviewed, the single committee method developed at Sullivan comes closest to shared decision making (CORE, 1995). All three processes used consensus negotiations as the primary means for reaching decisions. Only at Island Copper was this formally defined and intentionally used. At the others, consensus was undefined and operated informally. The processes were also qualitatively evaluated in terms of whether they fulfilled their own goals, were equitable, efficient, effective, and representative, and whether they promoted good public participation and contributed to good decision making. The processes mostly, fulfilled their own goals (as defined by their terms of reference). The processes are rated about the same with respect to procedural and distributional equity, effectiveness of outcome, representation, and promoting good public involvement. The Sullivan and Island Copper processes are rated relatively better than the Brenda process with respect to administrative equity, efficiency and process effectiveness. The Sullivan process, with half the number of meetings and exchanging written answers to questions in advance of meetings, minimized demands on participants. All three processes were well structured with respect to promoting good public involvement. However, judged by the norms of decision literature, the processes were relatively weak with respect to decision making. Problems were not defined, nor were interests or objectives. Empirical measures for goals or objectives were not identified. Few alternatives were proposed; nor were they evaluated in a way that could lead to a clear understanding of the trade-offs involved. Although few decisions were actually reached in the processes, their quality may be inferior because of these shortcomings. Notwithstanding these theoretical and empirical shortcomings, public involvement in each case found general support among government, industry, and public participants. Consequently the processes received a high degree of approval. It remains uncertain, however, whether more public involvement processes will be undertaken. Although, the province's mines ministry is formally committed to greater public involvement in reclamation decision making (MEMPR, 1991b), the ministry seems stretched to support even the two processes now underway (Brenda and Sullivan). Additional processes would require more resources than are currently allotted. As well, staff training, participant funding, professional facilitation, and clerical services could be improved. Further research is suggested, in particular applying techniques of decision analysis to public involvement processes to facilitate the making of informed and insightful reclamation decisions.

Thesis (M.S.)--University of Nevada, Reno, 2006. / "(August 2006)." Includes bibliographical references (leaves 85-87). Online version available on the World Wide Web. Library also has microfilm. Ann Arbor, Mich. : ProQuest Information and Learning Company, [2006]. 1 microfilm reel ; 35 mm.

Thesis (M.S.)--Ohio University, June, 2007. / Title from PDF t.p. Includes bibliographical references.

Thesis (M.Sc.)--University of Western Australia, 2006.

Thesis (M.Sc.)--University of Alberta, 2010. / Title from PDF file main screen (viewed on Apr. 23, 2010). A thesis submitted to the Faculty of Graduate Studies and Research in partial fulfillment of the requirements for the degree of Master of Science, Department of Renewable Resources, University of Alberta. Includes bibliographical references.

Thesis (Ph. D.)--Murdoch University, 2009. / Thesis submitted to the Faculty of Sustainability, Environmental and Life Sciences. Includes bibliographical references (p. 308-319).