EcoMENA

Methane (CH₄) is a key product of the anaerobic degradation of organic waste and represents one of the most critical environmental challenges associated with waste management systems, particularly landfills and controlled disposal sites. The formation, emission, and mitigation of methane from such systems have been extensively studied due to its high global warming potential and its significant contribution to anthropogenic greenhouse gas emissions. This work provides a comprehensive discussion of methane generation through anaerobic degradation processes and evaluates mitigation strategies, with a particular focus on flaring, which converts methane into carbon dioxide (CO₂), thereby reducing its climate impact.

The biodegradation of organic waste in natural and engineered environments such as landfills occurs through a sequence of microbiological processes governed by oxygen availability. Initially, freshly deposited waste undergoes an aerobic phase during which oxygen is consumed by microorganisms. As oxygen becomes depleted, the system transitions into anaerobic conditions, which favor the development of specific microbial consortia responsible for the breakdown of complex organic substrates [1].

Under anaerobic conditions, organic matter such as carbohydrates, proteins, and lipids is progressively decomposed through a series of biochemical stages: hydrolysis, acidogenesis, acetogenesis, and finally methanogenesis. Methanogenesis is the terminal step in this process and is carried out by methanogenic archaea that convert intermediate products such as acetate, hydrogen, and carbon dioxide into methane [2].

The overall biochemical reactions can be summarized as follows: complex organic matter is hydrolyzed into simpler molecules, which are fermented into volatile fatty acids and subsequently converted into methane and carbon dioxide. The resulting gas mixture, commonly referred to as landfill gas, typically contains approximately 50–60% methane and 40–50% carbon dioxide, along with trace amounts of other gases [3].

The production of methane in landfills is influenced by multiple factors, including waste composition, moisture content, temperature, pH, and landfill management practices. High organic content, adequate moisture, and mesophilic to thermophilic temperature ranges favor methanogenesis, whereas unfavorable environmental conditions can limit microbial activity and reduce methane yields [4].

Methane is a potent greenhouse gas with a global warming potential approximately 28 times greater than that of carbon dioxide over a 100-year time horizon, and up to 84 times greater over a 20-year period [1]. This high radiative forcing makes methane a critical target for climate change mitigation strategies.

Landfills are among the largest anthropogenic sources of methane emissions, contributing roughly 10–12% of global methane emissions [5]. These emissions result from the continuous anaerobic degradation of organic waste over extended periods, often spanning decades.

In addition to its direct contribution to global warming, methane plays a role in atmospheric chemistry, including the formation of tropospheric ozone, which is harmful to human health and vegetation. Furthermore, methane has a relatively short atmospheric lifetime (approximately 10–12 years), meaning that reductions in methane emissions can yield rapid climate benefits compared to carbon dioxide mitigation [1].

The environmental impact of methane emissions from landfills is compounded by the increasing global generation of municipal solid waste. With waste production expected to grow significantly in the coming decades, methane emissions from landfills are projected to rise unless effective mitigation measures are implemented [1].

Methane generation in landfills follows a temporal evolution characterized by distinct phases. After the initial aerobic stage, the anaerobic acid phase leads to the accumulation of organic acids and a decrease in pH. This is followed by a phase of rapid methanogenesis, during which methane production reaches its peak. Subsequently, methane generation declines as biodegradable substrates are depleted, and the system eventually stabilizes [1].

The transport and emission of methane from landfills are governed by complex interactions between production, oxidation, and physical transport processes. Methane can migrate through the waste matrix and escape into the atmosphere via diffusion, advection, or through cracks and fissures in the landfill cover [6].

Not all produced methane is emitted. A portion can be oxidized by methanotrophic bacteria in the landfill cover soils, converting methane into carbon dioxide before it reaches the atmosphere. However, this natural mitigation mechanism is often insufficient to offset the large quantities of methane generated [7].

Given the significant environmental impact of methane emissions, various mitigation strategies have been developed to reduce emissions from landfills. These strategies can be broadly categorized into waste reduction, gas capture, biological oxidation, and thermal destruction [3].

Reducing the amount of biodegradable organic waste entering landfills is one of the most effective long-term strategies. This can be achieved through waste segregation, composting, and anaerobic digestion in controlled facilities. However, such measures require substantial infrastructure and behavioral changes and may not be immediately feasible in all regions [3].

Landfill gas capture systems represent a widely implemented approach to methane mitigation. These systems consist of a network of wells and pipes that collect the gas generated within the landfill. The collected gas can either be used as an energy source or treated to reduce its environmental impact [4].

Biological oxidation systems, such as bio-covers and biofilters, enhance the activity of methanotrophic bacteria to convert methane into carbon dioxide. While effective under certain conditions, these systems are generally used as complementary measures rather than primary mitigation solutions [7].

Flaring is one of the most widely used and effective methods for mitigating methane emissions from landfills, particularly when energy recovery is not feasible. This process involves the controlled combustion of methane, converting it into carbon dioxide and water vapor. Although this reaction produces carbon dioxide, which is itself a greenhouse gas, the overall climate impact is significantly reduced because carbon dioxide has a much lower global warming potential than methane. As a result, flaring can reduce the greenhouse effect of methane emissions by more than 96% [8].

Flaring systems are typically classified into three main types : open flares, enclosed flares, and thermal oxidizers. Open flares are simple and cost-effective but offer less control over combustion conditions. Enclosed flares provide better control and can achieve destruction efficiencies exceeding 99%, while thermal oxidizers operate at higher temperatures for stricter emission requirements [8].

The effectiveness of flaring depends on several factors, including the efficiency of gas collection systems, the composition of the landfill gas, and operational conditions. In well-designed systems, methane capture efficiencies can range from 35% to 90%, while flaring destruction efficiencies can exceed 99% for enclosed systems [8].

While flaring significantly reduces the climate impact of methane emissions, it is not without environmental drawbacks. The combustion process can produce additional pollutants, including nitrogen oxides, sulfur dioxide, volatile organic compounds, and particulate matter, which may affect local air quality [8].

Furthermore, large-scale flaring activities contribute to carbon dioxide emissions, highlighting the importance of optimizing flaring practices and exploring alternative uses of captured methane, such as energy recovery when feasible [8].

A concrete example of methane mitigation through flaring can be found in controlled landfill sites in countries where regulatory frameworks for waste-to-energy remain underdeveloped. In such contexts, landfill gas is collected through a network of vertical wells and horizontal drains and directed toward enclosed flaring units. In several engineered landfills, methane generated from the anaerobic degradation of municipal solid waste is captured but not valorized energetically due to the absence of clear regulations governing grid injection, power purchase agreements, or financial incentives for renewable energy derived from waste.

In addition, even where partial regulatory elements may exist, electricity generation from landfill gas is often not cost-effective due to high capital and operational costs, relatively low and variable gas yields, and limited market incentives. As a result, the collected methane is systematically flared. This practice allows operators to significantly reduce greenhouse gas emissions by converting methane into carbon dioxide, while ensuring compliance with environmental protection requirements. Although the energy potential of the gas is not exploited, flaring provides an immediate, technically feasible, and cost-effective mitigation measure in the absence of a fully supportive regulatory and economic framework.

Despite these drawbacks, flaring remains a critical interim solution, particularly in regions where infrastructure for methane utilization is lacking. By converting methane into carbon dioxide, flaring provides an immediate and substantial reduction in greenhouse gas emissions, contributing to climate change mitigation efforts.

Bottom Line

The management of methane emissions from anaerobic degradation of organic matter requires an integrated approach that combines multiple strategies. Advances in landfill design, gas collection technologies, and monitoring systems can enhance methane capture and reduce emissions. In addition, the development of waste-to-energy technologies offers opportunities to utilize methane as a renewable energy source, thereby reducing reliance on fossil fuels and providing economic benefits. Policy and regulatory frameworks also play a crucial role in promoting methane mitigation by incentivizing gas capture and utilization.

Methane generation from the anaerobic degradation of organic matter is a fundamental process in waste management systems, particularly in landfills. While this process is a natural consequence of microbial activity, it poses significant environmental challenges due to the high global warming potential of methane. Mitigation strategies, especially gas capture and flaring, play a crucial role in reducing methane emissions. Flaring, by converting methane into carbon dioxide, offers an effective and widely applicable solution, achieving high destruction efficiencies and substantially lowering the climate impact of landfill emissions. However, long-term solutions require a comprehensive approach that combines technological, regulatory, and behavioral measures to minimize organic waste disposal and enhance methane recovery and utilization.

References

[1] Grégoire, D. S., George, N. A., & Hug, L. A. (2023). Microbial methane cycling in a landfill on a decadal time scale. Nature Communications, 14, 7402.

[2] Citrasari, N., Rachman, I., & Matsumoto, T. (2025). Sustainable methane emission reduction from landfills: The role of capture and flaring technologies. Journal of Sustainable Chemistry and Engineering.

[3] Tong, H., Cheng, T., Li, X., et al. (2025). Reduction of methane emissions through improved landfill management. Nature Climate Change, 15, 866–872.

[5] Quantifying methane emissions from landfilled food waste — U.S. EPA report (2024).

[6] Scharff, H., Soon, H.-Y., Taremwa, S. R., et al. (2024). The impact of landfill management approaches on methane emissions. Waste Management & Research, 42(11), 1052–1064.

[7] Zhang, C., Xu, T., Feng, H., & Chen, S. (2019). Greenhouse gas emissions from landfills: A review and bibliometric analysis. Sustainability, 11(8), 2282.

[8]RMI (2023). Waste Methane 101: Driving emissions reductions from landfills.