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Harris, Mark Anglin. "Some organic amendments for heavy metal toxicity, acidity and soil structure in acid-sulphate mine tailings /". Title page, contents and abstract only, 2000. http://web4.library.adelaide.edu.au/theses/09PH/09phh3148.pdf.
Pełny tekst źródłaWatkins, Deidre Ann. "An assessment of the environmental compliance monitoring capacity of the Department of Minerals and Energy, Eastern Cape". Thesis, Rhodes University, 2009. http://hdl.handle.net/10962/d1003848.
Pełny tekst źródłaStoll, J. A. E. "Mining in national parks : a case study : an integrated environmental evaluation of possible magnesite mining in Weetootla Gorge within the Gammon Ranges National Park, South Australia /". Title page, abstract and contents only, 1989. http://web4.library.adelaide.edu.au/theses/09ENV/09envs875.pdf.
Pełny tekst źródłaMadalane, Thembi. "The obligation to rehabilitate mining areas : post mining activities". Thesis, University of Limpopo (Turfloop Campus), 2012. http://hdl.handle.net/10386/905.
Pełny tekst źródłaThe study focuses on rehabilitation, since absence of proper rehabilitation process result in indelible damage to the environment. South Africa, like many other countries, is faced with many environmental problems caused by mining. These problems are particularly caused by, inter alia, abandoned mining areas without rehabilitation, inadequate environmental impact assessment after closure, inadequate financial provision for rehabilitation, and lack of monitoring and aftercare system after post mine closure. The study found that many Companies ignore laws governing prospecting, extraction and rehabilitation. The main purpose of this research is to investigate and recommend guidelines in the rehabilitation process so as to instil respect for the environment. The study therefore recommended strict legislation relating to environmental protection against mining.
Baartjes, Joan Charlaine. "Exploring the use of mineral corridors and stranded ore deposits in order to alleviate rural poverty and effect environmental and social change through a proposed rural development corridor in South Africa". Thesis, University of Fort Hare, 2011. http://hdl.handle.net/10353/389.
Pełny tekst źródłaEwart, Timothy Ian. "Acid mine drainage in the Gauteng province of South Africa : a phenomenological study on the degree of alignment between stakeholders concerning a sustainable solution to acid mine drainage". Thesis, Stellenbosch : Stellenbosch University, 2011. http://hdl.handle.net/10019.1/17978.
Pełny tekst źródłaENGLISH ABSTRACT: Ecosystems, and the very services and resources that they provide, are fundamental to our existence. Regardless, mankind shows scant regard for the biotic and abiotic components of the environment that serve as both sources and sinks for anthropocentric demands, practices and behaviours. Of these vital resources, perhaps the one that is most under threat is water which while crucial for growth and development around the globe, is rapidly becoming a scarce commodity. In South Africa - already a water-scarce country - this situation is further compounded by mining practices that are not only unsustainable, but also largely unregulated from an environmental perspective. Mining activities have resulted in the mass exposure of iron pyrite and heavy metals, both underground and on the surface. Upon exposure to weathering, the iron pyrite gives rise to sulphuric acid, which, in turn results in the mobilisation and concentration of toxic metals. Although this is a geological phenomenon, the increasing concentrations of toxic metals as a result of mining have exposed the Gauteng province to enormous environmental, social and economic risks. Concerning the risks, the research highlighted the following: - Although comprehensive research has been found relating to the physical attributes of acid mine drainage (AMD), very little is known of the health aspects associated with AMD. Of immediate concern is, the subsequent environmental and health implications stemming from the association between living organisms and heavy metals. - In the absence of such information, the credibility of current solutions is thus questionable. Of the solutions that have been proposed, most have been reductionist in approach and have only focused on dealing with the surface decant of contaminated water from predominately non-functioning mines. The health risks associated with radioactive and highly toxic waste have been down played or simply ignored (Albrecht, 2011). - The absence of a comprehensive solution also raises questions as to the assessment and decision-making process utilised to date by the Department of Water Affairs (DWA). - Both government and the private sector have allowed the AMD threat to amplify over the years. Their inaction has been facilitated by the poor enforcement of legislation and, clever manoeuvring by mining companies, in what can only be described as a mutually beneficial relationship between government and the mining industry. In stark contrast to the inaction of government and the private sector, environmental activists have been very vocal in calling for a solution to a number of the risks associated with AMD. This, together with the recent decant of AMD in the Western Basin, has culminated in a public outcry and prompted calls for a solution to the AMD threat. Government's response to this was a narrow and incomprehensive solution, which only served to further frustrate the different stakeholder groups. Where stakeholders have different themes as to the implications and thus solutions to the AMD threat on the Witwatersrand (as driven by the profiles of the different stakeholder groups), an appropriate solution will only be realised by adopting the following recommendations: - Government must show the necessary political will, to fully engage the threat of AMD and address their poor track record as regulator - their credibility has been skewed through their vested interests in the mining industry. - Having taken ownership of the AMD threat on the Witwatersrand, government must move to avert any immediate risks to human well-being. - Under governments' leadership, the capacity of all stakeholders must be addressed to facilitate a participatory trans-disciplinary review of the assessment mechanisms and facts, in order to reach a mutually acceptable solution(s) to the social and environmental impacts associated with mining activities - a solution that will ensure future environmental integrity, social development and economic growth.
AFRIKAANSE OPSOMMING: Ekosisteme, en die dienste en hulpbronne wat dit voorsien, is grondliggend aan die mensdom se bestaan. Tog toon die mensdom weinig respek vir die biotiese en abiotiese komponente van die omgewing, hoewel ons met ons behoeftes, praktyke en gedrag daarop staatmaak én daaraan afbreuk doen. Van hierdie lewensnoodsaaklike hulpbronne is die mees bedreigde waarskynlik water, wat – hoewel dit vir groei en ontwikkeling wêreldwyd van deurslaggewende belang is – spoedig besig is om ʼn skaars kommoditeit te word. In Suid-Afrika, wat in elk geval ʼn waterarm land is, word hierdie toedrag van sake vererger deur mynboupraktyke wat nie net onvolhoubaar is nie maar ook ongereguleerd. Mynboubedrywighede het gelei tot die massablootstelling van ysterpiriet en swaarmetale, sowel ondergronds as op die oppervlak. Wanneer ysterpiriet chemies verweer, vorm dit swawelsuurwater, wat op sy beurt toksiese metale mobiliseer en konsentreer. Hoewel dít ʼn geologiese verskynsel is, het hierdie verhoogde konsentrasies as gevolg van mynbou die Gautengprovinsie aan enorme omgewings-, maatskaplike en ekonomiese risiko’s blootgestel. Wat die risiko’s betref, beklemtoon hierdie studie die volgende: - Hoewel omvattende navorsing oor die fisiese kenmerke van suur mynwater (“acid mine drainage” – AMD) onderneem is, is weinig bekend oor die gesondheidsaspekte wat daarmee gepaardgaan. Wat tot dusver van onmiddelliker belang was, was die omgewings- en gesondheidsimplikasies wat daaruit voortvloei wanneer lewende organismes aan swaarmetale blootgestel word. - In die afwesigheid van sodanige inligting is die geloofwaardigheid van huidige oplossings dus twyfelagtig. Die meeste van die oplossings wat voorgestel is, is reduksionisties van aard en beklemtoon slegs die hantering van besoedelde water wat op die oppervlak uit hoofsaaklik onaktiewe myne sypel. Die gesondheidsgevare wat met radio-aktiewe en hoogs toksiese afval gepaardgaan, word geheel en al onderspeel of bloot misgekyk (Albrecht, 2011). - Die gebrek aan ʼn omvattende oplossing laat ontstaan ook vrae oor die beoordelings- en besluitnemingsprosesse wat die Departement van Waterwese oor die jare sowel as meer onlangs gevolg het. - Sowel die regering as die privaat sektor het toegekyk hoe die bedreiging deur suur mynwater oor die jare vererger. Dié gebrek aan optrede is aangehelp deur swak wetstoepassing sowel as slimmer bewimpeling deur mynboumaatskappye in wat eenvoudig as ʼn wedersyds voordelige verhouding tussen die regering en die mynboubedryf beskryf kan word. In skrille kontras met die regering en privaat sektor se traagheid het omgewingsaktiviste nog nooit geskroom om hul stem te verhef en op oplossings vir baie van hierdie risiko’s aan te dring nie. Dít, tesame met die onlangse uitvloei van suur mynwater in die Westelike Kom, het op openbare protes uitgeloop en aanleiding gegee tot oproepe om ʼn oplossing vir die bedreiging van suur mynwater. Die regering se antwoord hierop was ʼn eng, beperkte oplossing wat die verskillende belangegroepe slegs verder frustreer het. Aangesien belangegroepe (in ooreenstemming met hul uiteenlopende profiele) verskillende aspekte van die implikasies van – en dus ook die oplossings vir – die bedreiging van suur mynwater aan die Witwatersrand beklemtoon, sal ʼn toepaslike oplossing gevind word slegs deur die volgende aanbevelings te aanvaar: - Die regering moet die nodige politieke wil toon om die bedreiging van suur mynwater ten volle die hoof te bied, en moet daadwerklik verbeter op sy swak prestasiegeskiedenis as reguleerder, waarin hy heelwat geloofwaardigheid ingeboet het vanweë regeringsbelang by die mynboubedryf. - Nadat die regering sy verantwoordelikheid rakende die bedreiging van suur mynwater aan die Witwatersrand aanvaar het, moet hy dringend optree om enige onmiddellike gevare vir menslike welstand te voorkom. - Onder leiding van die regering moet die vermoëns van alle belanghebbendes betrek word ten einde ʼn deelnemende, kruisdissiplinêre beoordeling van die meganismes en feite te onderneem, om sodoende (ʼn) wedersyds aanvaarbare oplossing(s) vir die maatskaplike en omgewingsimpak van mynboubedrywighede te bedink – ʼn oplossing wat die integriteit van die omgewing, maatskaplike ontwikkeling en ekonomiese groei sal verseker.
Moshanyana, Lineo Grace. "The impact of environmental pollution on public health with specific reference to Sasolburg industrial area, South Africa". Thesis, Nelson Mandela Metropolitan University, 2013. http://hdl.handle.net/10948/d1018899.
Pełny tekst źródłaStoll, J. A. E. (Julie-Ann E. ). "Mining in national parks : a case study--An integrated environmental evaluation of possible magnesite mining in Weetootla Gorge within the Gammon Ranges National Park, South Australia". 1989. http://web4.library.adelaide.edu.au/theses/09ENV/09envs875.pdf.
Pełny tekst źródła"Assessing the effectiveness of current biodiversity offset strategies in South Africa : a case study on current perceptions and views in the mining industry". Thesis, 2015. http://hdl.handle.net/10210/13847.
Pełny tekst źródłaSouth Africa is exceptionally rich in biodiversity. South Africa has been recognized as the third most biologically diverse country in the world, and has three globally recognized biodiversity hotspots; namely the Cape floristic, the Succulent Karoo and the Maputaland-Pondoland regions (NSBA, 2004). South Africa’s seas straddle three oceans, and provide a range of habitats from cool water kelp forests, to tropical reefs and deep ocean abyss (NSBA, 2004). Unfortunately, due to various pressures, many ecosystems are in trouble: 34% of terrestrial systems, 82% of river signatures, 65% of marine biozones and 8 estuarine types are threatened (NSBA, 2004). Mining has been identified as one of the sectors impacting negatively on biodiversity; the other significant pressures being agriculture, afforestration, urban and industrial development, extractive fishing, alien invasives and climate change (NSBA, 2004). The concept of ‘biodiversity offsets’ is relatively new and there are only generic methods whichare ill suited to determine appropriate biodiversity offsets in the South African context. The rationale for biodiversity offsets in South Africa is two-fold: firstly, South Africa contains biodiversity that is unique globally; secondly, its ecosystems underpin socioeconomic development and delivery of important services such as the reliable supply of clean water, ecotourism and coastal protection. Land-intensive development poses a significant threat to the countries remaining biodiversity. South African policies have, over the past few years, increasingly prioritised the conservation of biodiversity and important ecosystem services (Department of Environmental Affairs and Development Planning, 2007). The motivation for this is a decline in global biodiversity (WWF & ZSL, 2012). Land use changes are the main motivation for identifying the need for creating a system within the planning process that tackles unavoidable and residual impacts to biodiversity. The implementation of EIA in South Africa in terms of the National Environmental Management Act (No. 107 of 1998) allowed for the formal evaluation of impacts to habitat, wildlife and other natural considerations to be done as a prerequisite for developers to receive approval for a project to go ahead (BBOP, 2000). The aim of this study was to compare the current South African biodiversity offset approach to that of offset banking and no net loss or net gain principles as a feasible and beneficial alternative. A structured interview process was conducted to ascertain current understanding and perceptions relating to biodiversity offsets, biodiversity offset guidelines and regulations, offset banking, relevant experience and perceptions to determine the current level of understanding in the mining sector and with environmental consultants. This aided in determining whether biodiversity offset practices in its current form in South Africa were understandable, can be implemented effectively and achieves the rationale of biodiversity offset banking.
Mosai, Alseno Kagiso. "Modelling of sorption of trace elements in an agricultural soil impacted by mining activities". Thesis, 2017. http://hdl.handle.net/10539/23522.
Pełny tekst źródłaThe development of the economy of South Africa and many other countries has been highly dependent on mining industries. Minerals such as gold, platinum, diamond and many others have been mined and continue to be mined. Despite the importance of these minerals, their processing comes with social and environmental problems. During the processing of these minerals, trace elements such as copper, chromium, nickel, mercury, uranium, molybdenum and many others are released as wastes into the environment either, directly or indirectly. The release of the elements into the soil is of concern due to the possibility of groundwater system contamination. The presence of these elements in the groundwater system poses serious challenges to the wellbeing of life forms, due to their toxicity, when they exceed threshold limits. From the processing plants, these elements could be released onto the soil, and mobilise to groundwater, increasing the already existing environmental crisis due to water pollution. Once these elements are in the water, access to living organisms becomes easier through the food chain. Some of these elements are not biodegradable and thus persist in the environment as well as in the bodies of living organisms. They can cause serious health problems because of their toxicity effect. In humans, these elements can be carcinogenic, and also cause chronic disorders, kidney failures, defects in infants, bone and vascular diseases which could also be lethal. It is therefore of importance that these elements are neither bioavailable nor bioaccessible to living organisms. When these elements are mobile in the soil, the probability of reaching groundwater increases. Water, an important natural resource should always be protected from such pollutants. The demand for unpolluted water has been rising every year in the world due to increasing population, extended droughts and improper disposal. This research was dedicated to determining the behaviour of elements in an agricultural soil impacted by mining activities. Agricultural soils are sometimes exposed to pollutants that could originate from dust fallout or precipitation; fertilisers and manure; pesticides; and water used for irrigation. Understanding the iv processes that control the distribution of these pollutants in agricultural soils is an important risk assessment measure, considering that such pollutants have the potential of being taken up by crops and vegetables or transported to groundwater. In this study, a soil on a farm that grows vegetables for commercial purpose. Cabbage, spinach, carrots and potatoes are some of the vegetables grown on the plot and sold to markets in Pretoria and Johannesburg. The plot is in the vicinity of smelting operations in the North West Province. The mobility of trace elements in the soil can be controlled, depending on the type and properties of soil. Hence in this research, the ability of the soil to adsorb elements entering the soil is studied. The batch experimental work was performed to determine the effect of pH, initial concentration (5 - 100 mg/L), competing ions (Fe3+, Ca2+, Co2+, Mg2+, K+, Ni2+ and Zn2+), fertilisers (ammonium nitrate, ammonium phosphate and calcium chloride) and plant exudates (acetic acid, citric acid and oxalic acid as well as ethylenediaminetetraacetic acid (EDTA) which is often used as proxy organic ligand (found in manure)) on the adsorption of cadmium (Cd), copper (Cu) and chromium (Cr) onto an agricultural soil. The PHREEQC geochemical modelling code was used to complement experimental methods in predicting processes and to further assess the leaching behaviour of the elements. Powder X-ray diffraction (PXRD) and X-ray fluorescence (XRF) were used to determine the mineralization of the soil. The structural features of the soil were determined using Fourier Transform Infrared spectroscopy (FTIR) and the element content was determined using Inductively Coupled Plasma Optical Emission Spectroscopy (ICP-OES). The point of zero charge (PZC) of the soil was found to be 8.3 and the cation exchange capacity (CEC) of 51.6 meq/ 100g. In the absence of fertilisers and plant exudates, the soil exhibited a similar high adsorption for elements at all initial concentrations by all the elements. Most (> 90%) of the elements were adsorbed within the first 3 minutes of contact with the soil. Langmuir, Freundlich and Dubinin-Radushkevich adsorption isotherms were used to describe the experimental data for the elements. Kinetic rates were modelled using pseudo first-order and pseudo second-order equations. Pseudo v second-order gave the best fit for all the elements (R2 >0.999) indicating chemisorption. The effect of pH on Cd and Cu was insignificant however, the adsorption of Cr decreased with pH. The presence of competing ions decreased the adsorption of cadmium more than that of the other analyte elements. The soil was generally effective in adsorbing and retaining the elements. However, the retention was highly dependent on elemental speciation and prevailing conditions e.g. pH (as in the case of Cu and Cr). Such changes in conditions would have implications for groundwater quality. The effect of plant exudates and EDTA was studied and the results showed that low molecular weight organic acids (LMWOAs) viz acetic acid (AA), citric acid (CA) and oxalic acid (OA) and EDTA significantly (p < 0.05) decreased the adsorption capacity of the elements onto the agricultural soil. AA had the least effect on the adsorption capacity of the elements whereas OA and EDTA strongly prevented the adsorption of the elements. Moreover, some of the elements which were already in the soil including those which were not under study such as Ca and Mg were desorbed from the soil by OA and EDTA. Thus, the mobility of the elements was increased by the presence of plant exudates, increasing groundwater contamination and consequently threatening the health of living organisms. Agrochemicals such as fertilisers, stabilizers and pesticides are constantly applied to agricultural soils to improve the fertility of the soil for better crop production however; their presence may affect the mobility and bioavailability of elements in the soil. The effect of ammonium nitrate and ammonium phosphate as well as calcium chloride on the adsorption of Cd, Cu and Cr onto an agricultural soil was studied. The effects of initial concentrations of the elements (5 – 50 mg/L), concentrations of fertilisers (0.01 – 0.1 mol/L) and pH (3 - 8) on the adsorption of Cd, Cu and Cr were studied. The initial concentration of the elements and the concentration of fertilisers had no significant effect (p > 0.05) on the adsorption capacities of Cu and Cr at pH 5. But, ammonium nitrate and calcium chloride decreased the adsorption capacity of Cd. The adsorption of Cd onto the soil was reduced as the concentration of fertilisers increased. The adsorption of Cd was lower than that of Cu and Cr at all pH values. The agricultural soil was found to vi be an effective adsorbent in preventing the mobility of Cu and Cr in the presence of fertilisers but not for Cd whose adsorption was significantly affected by the presence of ammonium nitrate and calcium chloride. A continuous flow fixed-bed column script with specified conditions simulating the natural environment was utilised in PHREEQC for column studies. The geochemical computer model PHREEQC can simulate solute transport in soil surfaces. The effect of initial concentration (100 and 300 mg/L) of the elements, column bed depth (5 and 10 cm) and pH (3, 5, 7 and 10) were considered in this study. The adsorption capacity was affected by initial concentration of the elements since the breakthrough curves at higher analyte concentrations were reached at lower pore volumes than at low concentrations. This can be attributed to the fast occupation of active sites of the soil at higher concentrations. The results from PHREEQC indicated that the conditions used would lead to the oxidation of Cr3+ to Cr6+ leading to the formation of HCrO4- and Cr2O72- which were not favoured for adsorption by soil surfaces due to high solubility. This could have potential implications on the quality of groundwater in regions with similar conditions. Thus, the leaching of Cr6+ onto the agricultural soil will be high in areas where remediation techniques are not applied. The changing of bed depth from 5 to 10 cm did not have an effect on the adsorption of the elements. The ability of the soil surfaces to adsorb Cd and Cu even at lower bed depth implies that the soil will be effective in preventing the leaching of the elements to groundwater due to strong surface interactions of the elements with the soil. The results from PHREEQC showed that the adsorption of Cd and Cr onto the soil surface was not affected by pH. The results for Cr were contradicting with those obtained from laboratory experiments which could be due to the conditions used in PHREEQC. The change in the speciation of Cu at basic conditions decreased the ability of Cu adsorption onto the soil surfaces. The Cu2+ was converted to Cu(OH)2 which were large in size and thus only a small amount could be adsorbed since the other adsorption sites were covered by the large species. This research had notable outputs in the form of publications which will form an important repository of information.
LG2017
Kekana, Mokoko Percy. "Non-occupational exposure to silica dust at ga-Maja village in Polokwane, Limpopo Province". Thesis, 2006. http://hdl.handle.net/10386/1383.
Pełny tekst źródłaStudies conducted on people who reside next to dust producing mines and industries show major health risks. Air pollutants from the mine and industries are inhaled by exposed miners and people who live in the vicinity (Steenland, 1995). Aim The aim of the study is to investigate non-occupational exposure to silica dust at gaMaja village in Polokwane, Limpopo Province. Methodology Study design For this study a cross sectional descriptive study design was used. Study site The study was conducted at gaMaja village near Polokwane in the Limpopo Province Sampling A total sample of 200 villagers participated in the present study. vi Data Collection Two hundred questionnaires were used to collect survey data and were coupled with four dust deposition gauges. The four gauges were mounted at four different positions in the village and were left for six hours. Data Analysis Questionnaires were analysed using SPSS computer software to determine silica-related illnesses and indicators of exposure to silicosis susceptibility. Dust samples from dust deposition gauges were analysed using a Varian 110 atomic absorption spectrometer for determination of silicon. Results The majority of both male and female participants reported that they do not wheeze (81.4%) or bring out phlegm from their chest (71.4%) as compared to those who reported episodes of cough (48%). Gauges were able to identify exposure to a particular pollutant, silica dust, and were successful.Discussion Data from questionnaires revealed that villagers do not show signs and symptoms related to silicosis, however, that does not rule out infection in a long run. The results from dust samples that were collected reveal that there are traces of silica (crystabolite) in the village of gaMaja. Dust samples were collected during normal production at the mine in the middle of summer. Conclusion Findings from this study show that people residing next to dust producing mines and industries are at high risk of health hazard. Mining companies and policy makers should take note of the findings while planning preventive strategies for reduction of air pollutants.
Titshall, Louis William. "Revegetation and phytoremediation of tailings from a lead/zinc mine and land disposal of two manganese-rich wastes". 2007. http://hdl.handle.net/10413/3512.
Pełny tekst źródłaThesis (Ph.D.)-University of KwaZulu-Natal, Pietermaritzburg, 2007.
"Environmental mining frameworks for water pollution in the Democratic Republic of Congo and the Republic of South Africa". Thesis, 2015. http://hdl.handle.net/10210/14017.
Pełny tekst źródłaVan, der Merwe Barend Jacobus Barnardt. "The impact of noise and ground vibration levels during mine construction at Chaneng Village, North-West Province". Thesis, 2014. http://hdl.handle.net/10210/12374.
Pełny tekst źródłaAny change in land-use goes hand-in-hand with changes in the prevailing ambient conditions such as a change in the prevailing environmental noise and ground vibration levels. This increase may have an impact on the health and well-being of people and may furthermore result in structural damage to houses. The level of exposure will depend on the type of activity, distance from the source and the attitude of the people exposed to the land-change activities. The main objective of this research was to identify, compare and determine what the impact of mine establishment could have on a residential area some 900m from the mine footprint area. The results of the survey would assist management in employing engineering control measures which would control the exposure levels. Mines are generally established in frontier regions where there are already formal and informal residential areas. These residential areas are usually in rural districts with low prevailing ambient noise levels or, if in fact perceptible, insignificant ones at the most. This study dealt with the evaluation of physical aspects such as environmental noise and ground vibration levels and the determination of exposure levels, an issue of environmental impact and of concern to public health. The village which is being exposed to increased noise and ground vibration levels is a formal housing area with infrastructural components such as roads, water and electricity connections. The exposure levels before and during the construction phase gave an indication of the positive or negative exposure levels that the people were enduring during the establishment phase of the mine...
Mahao, Tseliso John. "Assessment of changing urban dynamics in Johannesburg city regions as consequence of re-mining of the tailings dumps using Geographical Information System and remote sensing". Thesis, 2017. https://hdl.handle.net/10539/24029.
Pełny tekst źródłaThere is a growing interest in the reclamation of the old gold mines’ tailings dumps in Johannesburg city region driven by the economic value of the remaining gold resource. This reclamation activity is accompanied by various rehabilitation methods to reduce issues such as acid mine drainage and wind pollution. The impact of land use and land cover change (LULCC) can have an enormous impact on land development and planning. Monitoring of LULCC is very important in the planning and decision making processes. Remote sensing (RS) as the source of basic data for monitoring change is very highly recommended as tool to monitor changes occurring in the Johannesburg City Region as a result of rehabilitation and reclamation of the gold mines’ tailings deposits. The main aim of the study is to understand how the reclamation and rehabilitation of the historical tailings dumps in Johannesburg are changing land use patterns of the city and its precincts. The objectives are to quantify the changes in land use and land cover as the results of mining rehabilitation using Landsat earth observation data over a period of 30 years at five years intervals and; to recommend on how the land cleared of waste dumps could be used for looking at the surrounding environment spatially. Various Geographical Information Systems techniques are applied here for change detection analysis and monitoring of potential changes in urban dynamics patterns. The results show rate of rehabilitation and reclamation to be slow, taking several years to see a meaningful change. There is some form of bias towards transforming the reclaimed land into industrial zones as opposed to other activities. The success of tailings dumps rehabilitation through revegetation process is highlighted.
MT 2018
Tshilande, Tshilisanani. "The use of tree layer to assess impacts of coal mining on biodiversity in Mukomawabani Area, Mutale Municipality South Africa". Diss., 2016. http://hdl.handle.net/11602/357.
Pełny tekst źródłaMatangira, Peace Aaron. "Investigating climate change intervention strategies in opencast mining contracting and plant hire companies: a case of mutual construction company group of companies, South Africa". Diss., 2017. http://hdl.handle.net/10500/23270.
Pełny tekst źródłaCollege of Agriculture and Environmental Sciences
M. Sc. (Environmental Management)
Naidoo, Suvania. "Development actors and the issues of acid mine drainage in the Vaal River system". Diss., 2014. http://hdl.handle.net/10500/13932.
Pełny tekst źródłaDevelopment Studies
M.A. (Development Studies)
Mohomed, Farzana. "Environmental rights afforded to residents affected by mining activities: a case study in Hondeklip Bay". Diss., 2006. http://hdl.handle.net/10500/1511.
Pełny tekst źródłaJurisprudence
LL.M
Chavalala, Bongani. "Clean technology transition potential in South Africa's gold mining sector : case of Harmony's Kusasalethu Mine". Diss., 2014. http://hdl.handle.net/10500/13601.
Pełny tekst źródłaEnvironmental Sciences
M. Sc. (Environmental Management)