The constitutional democracy in South Africa, ushered in by the first democratic elections of 1994, has opened up opportunities for the rise of various issues that were previously marginalised. The current political dispensation, supported by new progressive legislation, has rendered reckless management of waste management unacceptable. As a result, the management of waste, particularly the dominant landfill site waste management facilities, has come under increasing scrutiny from civil society organisations, the public and affected communities. Whilst the new constitutional order has demarcated responsibility for the management of solid waste, reality indicates that in spite of various legislative attempts to ensure the institutionalisation of sound and integrated waste management, solid waste is still poorly managed by responsible authorities. It has also been evident that many municipalities in South Africa still rely on the problematic landfill sites as the dominant waste disposal facility, this despite the obvious environmental problems that land filling engenders. It has been noted that waste problems are still marginalised from the mainstream development initiatives of responsible municipalities. The poor management of solid waste and the negation of responsibility, as in the case in the Msunduzi Municipality, are indicative of the politics involved in the identification of policy issues that government attends to from the available pool of existing social concerns. The failure to find policy solutions to identified waste problems in the Msunduzi Municipality has provoked questions around how policy issues negotiate their way onto the government agenda. The biggest issue from a public policy perspective is how does government decide on which issues they will address amongst the numerous and equally pressing social problems that warrant government attention. Using Kingdon‟s agenda-setting theory, this dissertation found that problem definition, policy dynamics and political interests all play influential roles in the agenda status of social problems and whether they are addressed or not. As a result, the study argues that there must be positive interaction between the three, problem, policy and political streams, in order to produce a solution to the policy issues of waste management in the Msunduzi Municipality. / Thesis (M.Soc.Sc.)-University of KwaZulu-Natal, Pietermaritzburg, 2011.

The constitutional democracy in South Africa, ushered in by the first democratic elections of 1994, has opened up opportunities for the rise of various issues that were previously marginalised. The current political dispensation, supported by new progressive legislation, has rendered reckless management of waste management unacceptable. As a result, the management of waste, particularly the dominant landfill site waste management facilities, has come under increasing scrutiny from civil society organisations, the public and affected communities. Whilst the new constitutional order has demarcated responsibility for the management of solid waste, reality indicates that in spite of various legislative attempts to ensure the institutionalisation of sound and integrated waste management, solid waste is still poorly managed by responsible authorities. It has also been evident that many municipalities in South Africa still rely on the problematic landfill sites as the dominant waste disposal facility, this despite the obvious environmental problems that land filling engenders. It has been noted that waste problems are still marginalised from the mainstream development initiatives of responsible municipalities. The poor management of solid waste and the negation of responsibility, as in the case in the Msunduzi Municipality, are indicative of the politics involved in the identification of policy issues that government attends to from the available pool of existing social concerns. The failure to find policy solutions to identified waste problems in the Msunduzi Municipality has provoked questions around how policy issues negotiate their way onto the government agenda. The biggest issue from a public policy perspective is how does government decide on which issues they will address amongst the numerous and equally pressing social problems that warrant government attention. Using Kingdon‟s agenda-setting theory, this dissertation found that problem definition, policy dynamics and political interests all play influential roles in the agenda status of social problems and whether they are addressed or not. As a result, the study argues that there must be positive interaction between the three, problem, policy and political streams, in order to produce a solution to the policy issues of waste management in the Msunduzi Municipality. / Thesis (M.Soc.Sc.)-University of KwaZulu-Natal, Pietermaritzburg, 2011.

Waste is commonly disposed in landfills, this result in the formation of leachate which needs to be treated to acceptable standards before being discharged to the environment. High concentrations of pollutants, particularly ammonia, in the landfill leachate are persistent even after the closure of the landfill and it requires ad hoc treatment. Treated leachate can still be characterized by high concentrations of nitrates, which exceeds the discharge standards. This phenomenon is observed in the Mariannhill landfill site in Durban, where leachate is nitrified in a Sequencing batch reactor and produces effluent with over 1000 mg/l (Trois et al, 2010a). Denitrification can be used to remove nitrate concentrations, this process occurs under anoxic conditions in the presence of an external carbon source. Denitrification treatment methods utilize chemicals such as methanol and ethanol as carbon sources, but the large scale application of these chemicals is often uneconomical. This research aims at identifying the cost effective treatment system for bio-denitrification that utilizes commercial garden refuse (CGR raw and lightly composted for 10 weeks “CGR 10”) as carbon sources. The feasibility checks for applying these substrates were based on the efficiency and kinetics of nitrate removal over a short and long-term period, thus providing the estimates for operational procedures. Initial characterization tests, batch and column tests were performed in the lab towards achieving the aim of this research. All batch tests achieved 100% of nitrate removal, but CGR raw was faster than CGR 10 with a time difference of 16% and 20% for batches at 100 and 500 mg/L, respectively. The significant difference in the kinetic removal efficiency was observed in batch tests at 2000 mg/L, where CGR raw was about 18 times faster than CGR 10 and about 2 times faster than that of CGR raw at 500 mg/L. Thus, the kinetics of nitrate removal in CGR raw at 2000 mg/L was suspected to be due to chemical reaction other than biological reaction. In the second set of batch tests the kinetics of nitrate removal for CGR raw was about 3 times that of CGR 10. The column tests, which were operated as continuous flow reactor did not achieve full denitrification due to high flow rate applied. First set of column tests (columns A) used previously used substrates to treat synthetic nitrate solution (500 and 2000 mg/L). Second set of column tests (columns B) used fresh substrates to treat pre-treated landfill leachate with nitrate concentration of about 2000 mg/L. CGR 10 achieved better removal efficiency than CGR raw when treating synthetic solution. Whereas, CGR raw achieved better nitrate removal when treating pre-treated landfill leachate. Decrease in flow rate improved the removal efficiency of the substrates. Dilution of nitrified leachate to about 500 mg/L could improve the efficiency of the substrates. / Thesis (M.Sc.Eng.)-University of KwaZulu-Natal, Durban, 2011.

Landfill leachate treatment in South Africa is still in its early stages; research has been conducted but primarily at pilot scale level. Current legislation in South Africa does not prohibit the discharge of landfill leachate into the sewer line, despite the high risk of methane explosions and corrosion of the sewer pipes. Thus, to date, the off site channelling of landfill leachate into the sewer lines for further dilution in municipal wastewater treatment plants is the most common practice. Due to the development of stricter environmental regulations, the design of sustainable landfills is leading to the 'treatment at source' concept. Increasing public pressure is also forcing new landfills to be situated in remote areas where there is no avaliable sewer line to discharge into and 'treatment at source' will be required. Due to these developments, coupled with the lack of full scale leachate treatment experience in South Africa, Durban Solid Waste (The waste service unit of the Durban metropolitan), in an attempt to develop the knowledge and practical experience required for leachate treatment, undertook a research project to investigate the use of nitrification/denitrification pilot scale sequencing batch reactors (SBR) to treat leachate from the Bisasar Road and Mariannhill Landfills. The successful completion of the trials proved that the full removal of nitrogen compounds could be easily achieved, under South African climatic conditions, in a single sludge SBR system. The system was found to be simple to operate and required low maintenance. However, the final effluent required further treatment before it could meet the general discharge standards into natural watercourses. Being South Africa, a 'low gross income' country, it became necessary to consider an appropriate, cost effective and technically feasible 'polishing' treatment system. It was decided that a pilot scale treatment trial, using vegetated submerged bed constructed wetlands, be undertaken to assess the applicability and feasibility of such a passive system for the 'polishing' of the effluent from the pilot scale sequencing batch reactors. The wetland systems were found to be affected by many interrelating climatic factors. The trials concluded that the wetlands could not achieve the required discharge standards, in terms of concentration. However, it also showed that the effluent organics posed no oxygen demand or toxic threat to a receiving environment. The trials showed the ability of the wetlands to behave as mass removal systems, which could achieve the required mass removal efficiency in terms of mass output per day. / Thesis (M.Sc.Eng.)-University of Natal, Durban, 2003.

This study investigated the establishment of vegetation cover planted in plug and seedling form in the closure phases of the Umlazi Landfill. It also investigated the various facets of the closure process of the Umlazi Landfill and the effect these have on the establishment and choice of vegetative cover, and the grass technology used to make the establishment of vegetation a success. The setting up of trials and the gathering of basic data were undertaken to assess the alternative vegetation options available to researchers. The cover provided by the grasses was assessed in the investigation. The capping of landfill sites is a relatively new approach and it is soon to become a mandatory requirement by the Department of Water Affairs and Forestry (Minimum Requirements for Waste Disposal) (DWAF, 1998). This systematic investigation used in the closure of the Umlazi Landfill, will provide a model for the capping of landfills in South Africa. Seeing that this was the first hazardous (H:h) landfill site in the country to be closed according to the Minimum Requirements for Waste Disposal (DWAF, 1998), every attempt was made to ensure that all aspects in the closure of the site met with the Minimum Requirements. The Minimum Requirements document mentions only briefly that the landfill must be vegetated with some grass type. Prior to 1994, capped landfill sites were usually planted with traditional grass seed mixes and these were not widely successful, as seen on many older landfills that have been partially or completely capped, and where vegetation cover is sparse. There is much literature in the developed countries on the closure of landfills (e.g., Erickson, During the site inspections in June 2001 and February 2002, it was noted that many species of alien plants had established themselves in the poor soil conditions. This made it even more important to find indigenous vegetation to vigorously establish itself that would prevent the establishment of alien invaders. Samples of grass species established on some part of the site were also taken for identification. The dominant grass was identified as Cynodon dactylon. In view of establishing a balanced vegetative cover on top of the Umlazi Landfill, Acacia karoo trees (in seedling form) were also planted. Three bunch grass species, Melinis nerviglumis, Melinis minutiflora and Hyparrhenia hirta, were tested to see if thatching grass could be grown on the site to generate a cash crop for local residents of Umlazi township. Preparation and planting of the capped areas took place in the latter part of 2003 and were completed in early 2004. Measurements and field data were recorded and statistically analysed. The trials revealed three key findings: Firstly, both creeping grasses studied, namely Cynodon dactylon var. “Sea Green” and Panicum natalense var. ”Natal Buffalo Grass” grew well on the site. Initially P. natalense grew faster but after a month, C. dactylon overtook it. At the end of the trial (six months, P. natalense provided a higher level of soil cover. However, C. dactylon grew more consistently over this period. Hence both species provided good growth and cover on this site. Secondly the three bunch grasses, Melinis nerviglumis, Melinis minutiflora and Hyparrhenia hirta, all grew well and had similar survival rates. Hence the potential for growing these grasses as a cash crop has potential. Thirdly, all the Acacia karoo trees survived, i.e., they achieved 100% survival. The average height increase and stem width was similar in all trials and growth was consistent over the six month growing period. Hence the tree species would be a good choice for planting on landfills in its ecologically suitable zones. It is therefore feasible to envisage the planting of a mixture of grasses under the cover of A. karoo trees, to provide a balanced mixture of indigenous grasses to cover a freshly capped landfill. Such a system should provide for stable growth of vegetation for many years. / Thesis (M.Sc.)-University of KwaZulu-Natal, Pietermaritzburg, 2008