Biodegradation in Municipal Solid Waste landfills
- Biodegradation in Municipal Solid Waste landfills
- Solid Waste Composition and Management
- Landfills - a brief review
- Settlement in MSW Landfills
- Factors Influencing Landfill Settlement
- Biodegradation of MSW
- Biodegradation in Landfills
- Bioreactor technology - Its significance
- A Case Study - Performance of North American Bioreactor Landfills
- All Pages
Biodegradation of MSW
To understand the biodegradation of waste in landfills, it is important to understand the general pathway of anaerobic biodegradation which is a complex process that requires the coordinated activity of several trophic groups of microorganisms (Madigan et al., 2003).
The primary biodegradable constituents in MSW are cellulose (C) and hemicellulose (H), which comprise approximately 40–60% of MSW by dry weight and account for greater than 90% of its methane potential (Barlaz et al. 1990), while the other major organic component, lignin, is at best only slowly degradable under methanogenic conditions (Colberg, 1988). Reported cellulose, hemicellulose, and lignin concentrations in residential refuse range from 28.8 to 54.3%, 6.6 to 11.9%, and 12.1 to 28% of dry weight, respectively (Barlaz, 2006). Data on the cellulose, hemicellulose, and lignin concentrations in municipal waste components are summarized in Table 2.
Table 2. Chemical Composition and Ultimate Methane Yield of Solid Waste Components (Eleazer et al., 1997).
aData are based on measurements in 2-L reactors that were operated to maximize methane production.
Additional values represent samples tested in subsequent studies.
MSW decomposition is a microbially mediated process that occurs in sequential phases referred to as hydrolysis, fermentation/acidogenesis, acetogenesis, and methanogenesis (Farquhar and Rovers 1973; Zehnder 1978; Barlaz et al. 1989; Pohland and Kim 1999; Levén et al. 2007).
The first phase is the hydrolysis of polymers (carbohydrates, fats, and proteins), which yields soluble sugars, amino acids, long-chain carboxylic acids, and glycerol. Equation 1. shows an example of a hydrolysis reaction where organic waste is broken down into a simple sugar, in this case, glucose (Ostrem, 2004).
Equation 1 : C6H10O4 + 2H2O → C6H12O6 + 2H2
In the second phase, acidogenic bacteria transform the products of the first reaction into short chain volatile acids, ketones, alcohols, hydrogen and carbon dioxide. The principal acidogenesis stage products are propionic acid (CH3CH2COOH), butyric acid (CH3CH2CH2COOH), acetic acid (CH3COOH), formic acid (HCOOH), lactic acid (C3H6O3), ethanol (C2H5OH) and methanol (CH3OH), among other. From these products, the hydrogen, carbon dioxide and acetic acid will skip the third stage, acetogenesis, and be utilized directly by the methanogenic bacteria in the final stage (Figure 9). Equations 2, 3 (Ostrem, 2004) and 4 (Bilitewski et al., 1997) represent three typical acidogenesis reactions where glucose is converted to ethanol, propionate and acetic acid, respectively.
Equation 2 : C6H12O6 ↔ 2CH3CH2OH + 2CO2
Equation 3 : C6H12O6 + 2H2 ↔ 2CH3CH2COOH + 2H2O
Equation 4 : C6H12O6 → 3CH3COOH
In the third phase, known as acetogenesis, the rest of the acidogenesis products, i.e. the propionic acid, butyric acid and alcohols are transformed by acetogenic or fatty acid oxidizing bacteria into hydrogen, carbon dioxide and acetic acid (Figure 9). Hydrogen plays an important intermediary role in this process, as the reaction will only occur if the hydrogen partial pressure is low enough to thermodynamically allow the conversion of all the acids. Such lowering of the partial pressure is carried out by hydrogen scavenging bacteria. Equation 5 represents the conversion of propionate to acetate, only achievable at low hydrogen pressure. Glucose (Equation 6) and ethanol (Equation 7) among others are also converted to acetate during the third stage of anaerobic biodegradation (Ostrem, 2004).
Equation 5 : CH3CH2COO-+ 3H2O ↔ CH3COO-+ H++ HCO3-+ 3H2
Equation 6 : C6H12O6+ 2H2O ↔ 2CH3COOH + 2CO2+ 4H2
Equation 7 : CH3CH2OH + 2H2O ↔ CH3COO-+ 2H2+H+
The fourth and final phase is called methanogenesis. During this stage, microorganisms convert the hydrogen and acetic acid formed by the acid formers to methane gas and carbon dioxide (Verma, 2002).The most common methanogenic substrates are acetate and CO2 plus H2. The bacteria responsible for this conversion are called methanogens and are strict anaerobes. Most methanogens have a pH optimum around 7 (Zinder, 1993). Should the activity of the fermentative organisms exceed that of the carboxylic acid degraders and methanogens, there will be an imbalance in the ecosystem. Carboxylic acids and H2 will accumulate and the pH of the system will fall, thus inhibiting methanogenesis. Waste stabilization is accomplished when methane gas and carbon dioxide are produced.
Equation 8 : CO2+ 4H2→ CH4+ 2H2O
Equation 9 : 2C2H5OH + CO2→ CH4+ 2CH3COOH
Equation 10 : CH3COOH → CH4+ CO2
The general scheme of anaerobic substrate biodegradation and microbial community relationships is illustrated in Figure 9.
Fig. 9 Overall process of anaerobic decomposition (Madigan et al., 2003)
Fig 10. Schematic representation of the course of anaerobic methane generation from complex organic substances showing scanning electron micrographs of individual microorganisms involved (Source: Waste to Energy Research and Technolgy Council)
In the overall anaerobic decomposition process, hydrolysis is the rate-limiting step when the substrate is complex solid organic material (e.g., C and H), whereas methanogenesis is rate-limiting when the substrate is solubilized (Noike et al. 1985; Pavlostathis and Giraldo-Gomez 1991; Vavilin et al. 1996).
The decomposition phases of MSW have unique leachate chemistry and biogas characteristics that have been linked to time-dependent compression phases of mechanical creep and biocompression (Hossain et al. 2003; Olivier and Gourc 2007; Ivanova et al. 2008; Gourc et al. 2010). During initial hydrolysis, fermentation, and acetogenesis (i.e., acid formation phase), carboxylic acids accumulate in the leachate and the leachate hydrogen ion concentration (pH) decreases (Barlaz et al. 1989; Pohland and Kim 1999). Mechanical creep is dominant during the acid formation phase (Wall and Zeiss 1995; Ivanova et al. 2008). Biocompression coincides with methanogenesis, which is characterized by methane generation, acid consumption, and increasing leachate pH. The transition from dominant mechanical creep to dominant biocompression has been linked to the onset of methane generation and acid consumption (Olivier and Gourc 2007; Ivanova et al. 2008; Bareither et al. 2010; Gourc et al. 2010).