In USA, the Municipal Solid Waste (MSW) landfills accumulate about 130 million tons of solid waste every year. A significant amount of biodegradable solid waste is converted to landfill gas due to anaerobic stabilization by bacteria. These biochemical reactions produce volatile organic compounds (VOCs) like methane and others. Due to heterogeneity in refuse composition, unpredictable distribution of favorable environmental conditions for bacterial actions and highly uncertain pathway of gases, estimation of landfill gas emission for a particular landfill is complex. However, it is important to quantify landfill gases for health risk assessment and energy recovery purposes. This research is based on the monitoring and modeling methodology proposed by researchers at University of Central Florida is reported in this thesis. River Birch Sub-title D landfill, Westwego, LA was selected as the study area. The total emission calculated using the mathematical model ran on MATLAB is comparable with the result obtained from EPA LandGEM model, using historical waste deposition records

MENVSC / Department of Ecology and Resource Management / Over the years it has been observed that the solid waste sector has been an increasingly major contributor to the amount of Greenhouse gases (GHGs) in the atmosphere. To some extent a great chunk of these GHGs in the atmosphere is from Landfill gas (LFG). This study employs two theoretical models (LandGEM and Afvalzorg models) to estimate the amount of LFG emitted from Weltervenden and Thohoyandou landfill sites located in Limpopo province of South Africa. Furthermore, the study investigated the appropriate technique of the LFG utilisation as a source of electricity and the number of households using electricity. LFGcost model was used to estimate the cost and benefits related to the implementation of a LFG utilisation technology. Also, the possible health and environmental impacts of the landfill emissions on the people living closer to the landfill site were determined. The LandGEM model’s simulation concludes that CH4 and CO2 peaked in the year 2020 with values of 3.323 × 103 Mg/year and 9.118 × 103 Mg/year, respectively, for the Thohoyandou landfill. Results from the Afvalzorg model indicate that the CH4 peaked in the year 2020 with value of 3.501 × 103 Mg/year. Meanwhile the total emission of CH4 from 2005-2040 by the LandGEM and Afvalzorg models are 66200 Mg/year and 69768 Mg/year, respectively. However, for the Weltervenden landfill, the total LFG peaked in the year 2023 while the CH4 peak at 4061 Mg/year and 3128 Mg/year for LandGEM and Afvalzorg models, respectively. Furthermore, results from the cost analysis and benefits for the implementation of a LFG utilisation technology in both landfills show that the implementation of such a utilisation technology will be economically feasible considering the sale of t CO2 equivalent in the carbon market. However, without considering the sales of t CO2 equivalent, not all the LFG engines are economically feasible for both landfills. This study also shows that the residents living closer to the Thohoyandou landfill are at a higher risk of environmental pollution and could suffer negative impacts from the landfill than residents living far from the landfill site. However, the Weltervenden landfill did not have lots of communities living closer to the landfill and therefore it was not included in this study. / NRF