# 12.1: Anaerobic Digestion


## 12.1 Anaerobic Digestion

Anaerobic digestion (AD) is a biological process that breaks down organic materials (feedstocks) in the absence of oxygen (anaerobic conditions) into methane (CH4) and carbon dioxide (CO2). It is a process that occurs naturally in bogs, lake sediments, oceans, and digestive tracts. Cows contain one of the most well known fermentation vats, the rumen, which is part of the stomach (in other animals as well). Fermentation takes place during digestion! Figure 12.1 shows a schematic of anaerobic digestion.

There are benefits to using an anaerobic digester, particularly when raising livestock. A biogas, which contains methane and hydrogen, will be produced that can be used as a fuel. From a waste treatment point of view, it reduces the volume and mass of the waste, as well as reduces organic content and biodegradability of waste so that the residual matter can be better used as soil amendment and fertilizer. There are also environmental benefits: 1) odors and emissions of greenhouse gases (i.e., methane) and volatile organic compounds are reduced, and 2) the digester will destroy pathogens in the waste.

So, what are the biological processes that occur during AD? The bacteria ferment and convert complex organic materials into acetate and hydrogen. There are four basic phases of anaerobic digestion, which is a synergistic process using anaerobic microorganisms: 1) hydrolysis, 2) acidogenesis, 3) acetogenesis, and 4) methanogenesis. Figure 12.2 shows the progression and types of products for each phase.

## Hydrolysis Biochemistry

We have talked about hydrolysis in earlier lessons. Hydrolysis is a reaction with water. Acid and base can be used to accelerate the reaction. However, this occurs in enzymes as well. Figure 12.3 shows the hydrolysis reaction, and how cellulose, starch, and simple sugars can be broken down by water and enzymes. In anaerobic digestion, the enzymes are exoenzymes (cellulosome, protease, etc.) from a number of bacteria, protozoa, and fungi (see Reaction 1).

(1) biomass + H2O → monomers + H2

(Sources: cellulose, starch, sugars, fats, oils) (Products: mono-sugars [glucose, xylose, etc.], fatty acids)

## Acidogenesis Biochemistry

During acidogenesis, soluble monomers are converted into small organic compounds, such as short chain (volatile) acids (propionic, formic, lactic, butyric, succinic acids – see Reaction 2), ketones (glycerol, acetone), and alcohols (ethanol, methanol – see Reaction 3).

(2) C6H12O6 + 2H2 → 2CH3CH2COOH + 2H2O

(3) C6H12O6 → 2CH3CH2OH + 2CO2

## Acetogenesis Biochemistry

The acidogenesis intermediates are attacked by acetogenic bacteria; the products from acetogenesis include acetic acid, CO2, and H2. The reactions 4-7 shows the reactions that occur during acetogenesis:

(4) CH3CH2COO- + 3H2O → CH3COO- + H+ + HCO3- + 3H2

(5) C6H12O6 + 2H2O → 2CH3COOH + 2CO2 + 4H2

(6) CH3CH2OH + 2H2O → CH3COO- + 2H2 + H+

(7) 2HCO3- + 4H2 + H+ → CH3COO- + 4H2O

Several bacteria contribute to acetogenesis, including:

Syntrophobacter wolinii, propionate decomposer

Syntrophomonos wolfei, butyrate decomposer

Clostridium spp., peptococcus anaerobes, lactobacillus, and actinomyces are acid formers.

## Methanogenesis Biochemistry

The last phase of anaerobic digestion is the methanogenesis phase. Several reactions take place using the intermediate products from the other phases, with the main product being methane. Reactions 8-13 show the common reactions that take place during methanogenesis:

(8) 2CH3CH2OH + CO2 → 2CH3COOH + CH4

(9) CH3COOH → CH4 + CO2

(10) CH3OH → CH4 + H2O

(11) CO2 + 4H2 → CH4 + 2H2O

(12) CH3COO- + SO42- + H+ → 2HCO3 + H2S

(13) CH3COO- + NO- + H2O + H+ → 2HCO3 + NH4+

Several bacterial contribute to methanogenesis, including:

Methanobacterium, methanobacillus, methanococcus, and methanosarcina, etc.

As you can see, the bacteria for anaerobic digestion are different from other enzymes for making biofuels, and could even be in our own stomachs!

Any kind of organic matter can be fed to an anaerobic digester, including manure and litter, food wastes, green wastes, plant biomass, and wastewater sludge. The materials that compose these feedstocks include polysaccharides, proteins, and fats/oils. Some of the organic materials degrade at a slow rate; hydrolysis of cellulose and hemicellulose is rate limiting. There are some organic materials that do not biodegrade: lignin, peptidoglycan, and membrane-associated proteins. The organic residues contain water and biomass composed of volatile solids and fixed solids (minerals or ash after combustion). And it’s the volatile solids (VS) that can be non-biodegradable and biodegradable.

As we discussed regarding pretreatment of biomass for making of ethanol, efficiency of anaerobic digestion improves with pretreatment. Hydrolysis of cellulose and hemicellulose (phase 1 in AD) is improved with pretreatment because it overcomes biomass recalcitrance. As discussed in a previous lesson, pretreatment options include treatments with acids, alkalines, steam explosion, size-reduction, etc. Common alkaline agents include: NaOH, Ca(OH)2, and NH3.

Theoretical methane yield (YCH4, m3 STP/kg substrate converted) can be calculated from the elemental composition of a substrate:

CcHhOxNnSs

YCH4 = $$\dfrac{22.4 (\frac{c}{2} + \frac{h}{8} + \frac{x}{4} - \frac{3n}{8} - \frac{s}{4})}{12c+h+16x+14n+16s}$$

Table 12.1 shows the substrate, a common elemental formula, and the theoretical methane yield for each.

Table 12.1: Theoretical methane yield (m3 STP/kg substrate converted) for several biomass sources (Credit: Frigon and Guiot, 2010)
Substrate Elemental formula

Theoretical methane yield

(m3 STP/kg)
Carbohydrates (CH2O)n 0.37
Proteins C106H168O34N28S 0.51
Fat C8H15O 1.0
Plant biomass C5H9O2.5NS0.025 0.48

Figure 12.4 shows the biogas yield for several different feedstocks in m3/ton. Be aware that after digestion, there is a biogas yield and the remainder of the digestion, known as digestate. The biogas typically contains 50-60% CH4, with the rest primarily composed of CO2 and other trace gases. The digestate contains fiber, nutrients, and water, and these can be used for compost, animal bedding, and composite boards. Figure 12.5 shows a schematic of the components of the digester.

There are several factors that will affect anaerobic digestion. Different feedstocks will degrade at different rates and produce different amounts of methane (as seen in Figure 12.4 and Table 12.1). That depends on the biological degradability and methane potential, the carbon and nutrients available, and the moisture content of each feed material. As noted in Figure 4 and Table 12.1, fats contain the highest volatile solids and can generate the greatest amount of biogas. Solids take a longer time to digest than feedstocks that are soluble. Nutrients are also important. A suitable carbon to nitrogen ratio (C/N) is less than 30, and the carbon to phosphorous ration (C/P) should be less than 50. For example, lignocellulosic biomass has a high C/N ratio, so nitrogen sources must be added. Nutrients also must be free of toxic components. Other factors that can influence digestion are the availability and location of feed materials (transportation costs involved here), logistics of how to get materials to certain sites, and if size reduction is going to be necessary.

Digester performance will also depend on the microbial population in the digester. This means maintaining adequate quantities of fermenting bacteria and methanogens. A recycled stream is used to take a portion of the liquid digestate as inoculum (material used for inoculation of feed materials). And depending on feeds, there may be an acclimation period to reach acceptable conditions.

There are also variations in the operational factors and environmental conditions of the digester. It is important to know the total solids (TS) and volatile solids (VS) in the feeds, the best retention times, and to provide mixing. Operational factors include the amount and strength type of feedstocks added to the digester. The operation also depends on maintaining the microorganism population and organic loading in reactors, whether operating in a batch or continuous reactor. Mixing is also an important factor in any reaction. The goal of mixing is to keep the microorganisms in close interaction with the feed and nutrients. Mixing also prevents the formation of a floating crust layer, which can reduce the amount of biogas percolating out of the slurry. Mixing will benefit the breakdown of volatile solids and increase biogas production, but keep in mind mixing adds energy cost, so this must be balanced. The types of mixing in this system include gas bubbling and/or mechanical mixing.

Environmental conditions include the temperature and pH of the reactor, as well as concentrations of materials, including the volatile fatty acids, ammonia, salt, and cationic ions. Different methanogens react in temperature ranges. The type of methanogens that produce the most biogas are thermophiles, but the digester must be operating between 40-70 °C. Methanogens also prefer neutral pH conditions (6.5-8.2). Accumulation of volatile fatty acids (VFAs) can cause the digestion to stop producing gas – this happens when too much digestible organic material is added, a toxic compound is added, or there is a sudden temperature change. Toxic materials include: 1) oxygen, 2) antibiotics, 3) cleaning chemicals, 4) inorganic acids, 5) alkali and alkaline earth salt toxicity, 6) heavy metals, 7) sulfides, and 8) ammonia. An additional reason for AD process failure has to do with the reaction within being out of balance. In particular, the rate of acid formation and methane production should be equal. This is done by maintaining definite ranges and ratios of the following: solids loading, alkalinity, temperature, pH, mixing, and controlling VFA formation. When the methanogen microorganisms cannot keep up with the fermenting bacteria, the digester becomes acidic – also known as “sour.”

An ambient temperature liquid phase AD reactor is called a covered lagoon. Advantages of the covered lagoon are the low cost, ease of construction, and control of odor control with manure storage. Disadvantages include difficult sludge removal and only seasonal production. However, there are several designs that have controlled temperature, and are typical to different types of reactors: 1) complete mixing, 2) plug flow, 3) sequencing batch, and 4) fixed film. Table 12.2 shows a comparison of the variables for each type of anaerobic digester configuration.

Table 12.2: Comparison of various types of anaerobic digester configurations (Credit: On-Farm Anaerobic Digester Operator Handbook. M.C. Gould and M.F. Crook. 2010. Modified by D.M. Kirk. January 2010.)
Characteristic Covered Storage Plug Flow Digester Mixed Plug Flow Digester Complete Mix Digester Fixed Film Digester Induced Blanket Digester Two- Stage Digester
Digestion Vessel Clay or synthetic lined storage Rectangle tank in ground Rectangle tank in ground Round/square in/above ground tank In/above ground tank In/above ground tank In/above ground tank
Level of technology Low Low Medium Medium Medium High High
Added heat No Yes Yes Yes Optional Yes Yes
Total solids 3-6% 11-13% 3-13% 3-10% 2-4% <8% ~5%
Solids characteristics Coarse Coarse Medium Coarse Coarse Fine .. ..
Retention time(days) 60+ 15+ 15+ 15+ <4 3-5 10-13
Farm type Dairy, Swine Dairy, Swine Dairy, Swine Dairy Dairy, Swine Dairy, Swine Dairy, Swine
Optimum location All climates All climates All climates All climates Temperate/warm All climates All climates

This page titled 12.1: Anaerobic Digestion is shared under a CC BY-NC-SA 4.0 license and was authored, remixed, and/or curated by Hilal Ezgi Toraman (John A. Dutton: e-Education Institute) via source content that was edited to the style and standards of the LibreTexts platform; a detailed edit history is available upon request.