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Enteric Methane Emissions and Abatement Approaches: A Review

Vipul Kashyap Chand Ram Grover Sachinandan De Rohit Panwar Sunita Verma
Vol 8(11), 1-21
DOI- http://dx.doi.org/10.5455/ijlr.20180208090406

Production of enteric methane through microbial fermentation in ruminants has created attention, for its role as a greenhouse gas and loss of feed energy to the animal. The development and commitment to mitigate methane emissions are likely to influence the productivity of livestock systems, comprising animal nutrition. Curbing rumen methanogenesis is conceivable using advanced mitigation policies and their viability for practical applications are being researched around the world. It is possible to modify the microbial ecosystem of rumen to decrease the production of methane, but the manipulation of microbial components of the system has to be considered in an integrated way which differ in terms of viability, cost, and acceptance by end users. Therefore, their implementation should be based on the capacity to reduce methane emissions along with economic sustainability and improvement in animal performance. The present review highlights the enteric rumen methanogensis and strategies to mitigate the level of methane production.


Keywords : Global Warming Methane Mitigation Rumen Methanogenesis

Climate change, due to large scale industrialization has drawn worldwide attention. The rise in global human population, unlimited use of fossil fuels and urbanization are the key reasons for increased atmospheric concentration of greenhouse gases. These changes have led to global warming and depletion of ozone layer, have increased the penetration of ultraviolet rays, which is a great threat to the mother earth. Global warming has occurred over the past 120 years and has been especially rapid in the last 20 years. Among the various GHGs, carbon-dioxide (CO2), nitrous-dioxide (NO2), methane (CH4), tropospheric ozone, trichlorofluoromethane (CCl3F) and dichlorodifluoromethane (CCl2F2) accumulating at a rate of 0.3-0.9% annually and methane is the second major GHGs among all of them (Patra, 2012). Moreover, it has been reported that globally 15% of total methane emits from rumen, where 2-12% of the ingested feed energy is lost as CH4 (Knapp et al., 2014).

India’s livestock represents one of the largest zone in the world having a total of 529 million livestock, which makes India the largest contributor to global CH4 emissions (FAO, 2007). Yet, approximately 90% of cattle and buffalo are native breeds having low productivity. Indian livestock region produces nearly 12Tg of CH4 annually, of which more than 90% is emitted through enteric rumen fermentation (Chhabra et al., 2013; Forabosco et al., 2017). This is much higher than CH4 emissions from the US livestock sector i.e. 7.85Tg yr-1 (Hristov et al., 2014). The livestock sector of India accounts for 78% of total CH4 emissions from the agriculture sector and about 50% of CH4 emissions from all sectors in India (Swamy and Bhattacharya, 2006). Cattle have been documented to be a significant contributor of methane i.e. 53.5% trailed by buffalo (39%), goat (4.7%) and subsequently sheep (1.8%), where annual methane production by Indian livestock sector was estimated to raise by 15×109 kg in 2050 (Singhal et al., 2005; Patra, 2014).  Representing Indian scenario, methane emissions related to livestock sector can cause increase in surface temperature up to 0.7-0.036 mili kelvin (mK) over the 20 and 100 year time periods correspondingly, which is crucial step for India to achieve its GHGs emissions reduction goals (Kumari et al., 2018). Understanding the current tendency, as well as impending projections of CH4 emissions it is very important to identify policy gaps and to implement long-term policy mechanisms to reduce CH4 emissions. Although a very limited data for representing studies concerning future prediction related to Indian livestock are available (ALGAS, 1998; Yamaji et al., 2003; Singh et al., 2012; Pathak et al., 2013).

Microbiota of Rumen

Ruminants in India are served mainly on the diet containing high lignocellulosic agricultural by-products that mainly composed of cellulose, hemicellulose, lignin, starch, and protein. The rumen comprise various types of bacteria which are degrading these feed components. They interact among themselves and with other microbial groups to perform a synergistic effect on the production of volatile fatty acids and microbial proteins inside the rumen. Some of the common features of bacteria that reside in the rumen of animals fed on high roughage diet are as follows

(a) Majority of the bacteria are Gram-negative, however, number of Gram-positive bacteria tends to increase on the increment of high-energy diets in the ration.

(b) Most of the bacteria are obligate anaerobes.

(c) Some of them are so sensitive to oxygen that these are killed upon exposure to oxygen.

(d) A few rumen bacteria require a very low redox potential indicating their high degree of anaerobiosis and grow at a redox potential of lower than –350 mV. The bacterial community residing the rumen is enormously diverse. The majority of these microbes have not yet been cultivated; however, development of molecular tools have estimated that bacteria alone belonged to at least 300-400 phylotypes containing, 5.0 × 106 to 6.0 × 107 CFU/mL rumen liquor of the total bacterial population (Nathani et al., 2013).

In addition, protozoa, fungi, methanogenic archaea and bacteriophages also contribute to diversity and functioning of the rumen microbial ecosystem. Rumen ecosystem consists > 50 genera of bacteria with a cell population 1010-1011 CFU/mL in ruminal fluid, 25 genera of ciliate protozoa (104-106 /mL), five genera of anaerobic fungi (103 – 105 zoospores /mL) and 108-109 PFU/mL of bacteriophages (Kamra, 2005). The extent may even be higher as many of the microorganisms residing in the rumen are non-culturable.

Bacteria                                

The rumen micro-biome is highly variable and change in feed components also result changes in diversity of microbial population. The environment of the rumen is strictly anaerobic which limit growth of invading microorganisms due to high buffering capacity and osmotic pressure. Some of the rumen microbes produce antimicrobial compounds which inhibit the growth of other microbes present in the eco-system (Odenyo et al., 1994). For optimum growth of microbes, rumen provide favorable temperature (39°C) and pH (6.0-6.9), respectively. Bacteria responsible for cellulose degradation in ruminal fluid comprised Fibrobacter succinogenes, Ruminococcus albus, and Ruminococcus flavefaciens (Sahu et al., 2004).

Protozoa

Cilliate protozoa of rumen were classified into two groups i.e. entodiniomorphid protozoa and holotrich protozoa (Hungate, 1986). Holotrich protozoa comprise different enzymes like invertase, polygalacturonase in huge quantities. Interestingly, some of the holotrich protozoa also carry enzymes for degradation of hemicelluloses and cellulose but the amount present are relatively low as compared to that in entodiniomorphid protozoa (Williams and Coleman, 1985). Major groups of ciliate population in cattle and buffalo include Entodinium, Elytroplastron, Ostracodinium, Isotricha, and Dasytricha (Leng et al., 2011). The key role of ciliate protozoa in the rumen is stabilization of pH as rumen is always having low pH (Santra et al., 1995). Elimination of cilliate protozoa from rumen resulted in decrease in ammonia nitrogen and methanogenesis (Newbold et al., 2015).

Fungi

The presence of obligate and anaerobic fungi play a significant role in the degradation of fibrous diet with help of their various enzymes (Paul et al., 2003). It was observed that the diet possess high fiber content stimulate the growth of ruminal fungi as compared to the diet enriched in carbohydrates (Kamra et al., 2003). Fungi get access very easily into the lignocellulosic diet due to the presence of different enzymes like cellulases, hemicellulases, proteases, and esterases as compared to the cellulose-degrading bacteria (Fonty and Joblin, 1990).

 

Bacteriophages

Bacteriophages are responsible to infect specific bacteria which are not beneficial at different feeding regimes. Studies on bacteriophage role to infect bacteria indicate that Siphophages can infect methanogens viz, Methanobacter, Methanobrevibacter, and Methanococcus species but these have not been isolated from the rumen (McAllister and Newbold, 2008). Hence bacteriophage can be used as an alternative approach to control the increasing population of methanogens in the rumen. However, relative abundance of prophage i.e. 0.1 % in Phylum Euryarchaeota have been observed in metagenomic study of phage-bacterial interactions (Miller et al., 2012). Another limiting factor is that bacteriophage are host specific in nature. Rumen comprise of a large population of methanogens as compared to bacteriophage, therefore unable to deal with such situation, which is a major drawback in using this strategy to reduce methane (Janssen and Kirs, 2008).

Microbial Fermentation in Rumen

The rumen provides an anaerobic and methanogenic environment, where CO2 and H2 are produced from the fermentation of feeds, where they act as electron acceptor and donor (Fig. 1). In this environment, organic matter get degraded by the activity of different groups of anaerobes consisting of primary and secondary fermenters. The primary anaerobic fermenters degrades the monomers which were initially ingested by the animal in form of organic polymers. These monomers are further converted into volatile fatty acids, CO2 and H2 by both the primary fermenters and secondary fermenters.

Fig. 1: Schematic microbial fermentation of feed polysaccharides and H2 reduction pathways in the rumen (Morgavi et al., 2010).

The synthesis of methane contributes to the efficiency of the system where it avoids an increase in the partial pressure of H2 to a stage that might interfere the path for the usual functioning of microbial enzymes that are involved in electron transfer reactions, especially NADH dehydrogenase which results in the accumulation of NADH and eventually reduce rumen fermentation. The capturing of the H2 formed by one microbial species and used by another is normally referred as interspecies H2 transfer and this phenomenon includes a syntrophic association between two microorganisms (Wolin et al., 1997). Type of feed and occurrence of electron acceptors excluding CO2 in the rumen have a major effect on the presence and activity of H2 producers and utilizers. This well-known pathway other than methanogenesis can also consume H2 and thus potentially compete with methanogens and decrease methanogenesis in the rumen.

Ruminal Methanogenesis

Livestock has become a livelihood of millions of dairy farmers both in developed and developing nations. Ruminants belong to tropical countries such as India mainly rely on highly fibrous plant resources as feed, where these are utilized in rumen followed by their breakdown via multifarious microbial population (Sirohi et al., 2012; Balamurugan et al., 2018). The rumen customs into a greater portion of the reticulo-rumen, which is an effective chamber to retain ingested feed stuff (Russell and Rychlik, 2001). Large particles of digest are propelled up into the esophagus and mouth during contractions of the reticulum. Ruminants thus provide suitable habitat and a continuous supply of fresh nutrients to fibrolytic rumen microorganisms that convert plant cell wall polysaccharides into fermentation products such as protein, vitamins, volatile fatty acids i.e. acetic, propionic, butyric and short chain organic acids and these are absorbed across the rumen epithelium (Mitsumori and Sun, 2008). The rumen microbes such as, bacteria, fungi, and protozoa along with their fiber degrading enzymes help the fibrous plant materials to get digested, where microbial proteins are responsible to create maximum amino acids reaching to the small intestine (Janssen, 2010). A variety of rumen bacteria produce end products including formate and hydrogen which are subjected to secondary fermentation by other microbial species (Mitsumori and Sun, 2008). The rumen provide strict anaerobic habitat in which substrates are partially oxidized. Thus, removal of hydrogen gas derived from reducing equivalents (NADH), is a critical feature of rumen fermentation, since the build-up of hydrogen with the rumen is thermodynamically unfavorable for plant fiber fermentation (Morgavi et al., 2010). Rumen methanogens are capable of using hydrogen, formate, and methanol to produce methane via a pathway coupled to ATP synthesis. Efficient hydrogen removal by methanogens has a profound effect on the functioning of the rumen fermentation system as the build-up of hydrogen inhibits the re-oxidation of co-enzymes involved in redox reactions with in bacterial cells creating a less favorable environment for volatile fatty acid formation (Janssen, 2010).   Methanogens produce methane mainly by using two major substrates; CO2 and methyl group containing compound. The hydrogenotrophic methanogens that use CO2 as their carbon source and hydrogen as the main electron donor play a prominent role during methanogenesis in the rumen (Fig. 2).

Fig. 2: Enzymatic pathway for the formation of methane in methanogens. Formyl- MF, formylmethano-furan; Formyl-H4MPT, N5-formyl-tetra-hydromethanopterin; Methenyl-H4MPT, N5, N10-methenyl-tetra-hydromethanopterin; Methylene-H4MPT, N5, N10-methylene-tetra-hydromethanopterin; Methyl-H4MPT, N5 methyl-tetra-hydromethanopterin; Methyl-S-CoM, methyl coenzyme M; F420, coenzyme F420; F420H2, reduced coenzyme F420; H4MPT, methanopterin; H-S-HTP, N-7-mercaptohetanoyl-O-phospho-L-threonine; X named as unidentified electron donor (Attwood and McSweeney, 2008).

During the oxidation of sugars via the EMP pathway in bacteria, fungi and protozoa, electron carrying cofactors such as NADH must be reoxidized to NAD+ to allow fermentation to carry on. Under the anaerobic conditions of the rumen, where it is impossible to use oxygen as an acceptor of electron transfers to regenerate NAD+, the reduction of CO2 permits recycling of reduced cofactors (Morgavi et al., 2010). In hydrogenotrophic methanogenesis, CO2 is initially carried by methanofuran and reduced to formate. The electrons involved in this first step are donated by ferrodoxin reduced with H2. The formyl group from formyl tranferase is transferred to tetrahydromethanopterin (H4MPT), forming formyl-H4MPT in a reaction catalyzed by formyl methanofuran: H4MPT-formyl transferase. The formyl group then positively reduced to methenyl- H4MPT and then to methylene-H4MPT in a reaction catalyzed by 5, 10-methenyl H4MPT cyclohydrolase and methylene-H4MPT: coenzyme F420 oxidoreductase, respectively. In the next step, a reaction catalyzed by methyl-H4MPT: HSCoM methyltransferase transfers the methyl group to H4MPT, forming methyl- H4MPT. Methyl-CoM is reduced to methane by methyl coenzyme M-reductase in the last phase of methanogenesis. Substrate, methyl-coenzyme M (methyl-SCoM, 2- (methylthioethanesulfonate) and coenzyme B (CoBSH, N-7-mercaptoheptanoylthreonine phosphate) are transformed to methane and a heterodisulfide (CoBS-SCoM) and afterwards reduced to generate the CoB-SH and CoM-SH thiols. The methyl transfer from H4MPT and CoM as well as reduction of heterodisulfide are both exergonic reactions that are highly encouraging for ATP synthesis (Liu and Whitman, 2008).

Mitigation Strategies for Rumen Methanogenesis

Methane is a potent greenhouse gas that has a high urgency for mitigation because of its harmful global warming effect and because of its combination with tropospheric ozone and carbon, it becomes lethal that could reduce the life expectancy of 3.1 billion people worldwide (USEPA, 2014). Under usual feeding conditions, CH4 production is an unavoidable consequence of the fermentation of organic matter (OM) in the digestive tract of ruminants. Theoretically, the generation of CH4 in the rumen can be reduced by following ways

(1) Promoting a shift in fermentation in such a way that it could generate more reduced volatile fatty acids (VFAs), e.g. propionate, acetate, fumarate, and butyrate;

(2) Enrichment of animal diet with significant amount of rumen degraded protein, so that this fraction of protein could be used directly by rumen microorganisms;

(3) Addition of feed additives that inhibit methanogenesis e.g. bromochloro methane (BCM) or compounds which can favor bioreduction e.g. long-chain unsaturated fatty acids;

(4) Immunization against methanogens;

(5) Defaunation (removal of protozoa population of the rumen), as protozoans are represented as the hydrogen fuel supplier to methanogens;

(6) Stimulation of the growth of bacteriophages that infect and lyse methanogens;

(7) Supplementation of diet with compounds that exactly promote the growth of bacteria and/or archaea that utilize compounds such as nitrates and sulfates and have a higher affinity for H2 than methanogens;

(8) Direct-fed microbial (DFM), a new approach have been focused recently, which include the use of live, naturally occurring microorganisms.

Any method or technique which are quite stable and effective to lower on-farm CH4 emissions should be practical and must not have negative effect on the viability of ruminant livestock production. Alteration in diet arrangement to encourage useful modifications in rumen fermentation characteristics remains the most feasible approach to reduce the level of methane production. Dropping CH4 production per unit product over the lifespan of a ruminant should be seen as the major objective to reduce the GHG emission from livestock sector. This highlights the need for integrated solutions that result in improved digestive efficiency, reproductive performance and animal health to extend the productive lifetime of growing or lactating ruminants. Some of the effective methane abatement strategies are enlisted in Table 1.

Alternate Hydrogen Sinker as Direct Fed Microbial (DFM)

Management of H2 inside the rumen is the most important aspect to be taken into consideration while developing strategies to control ruminant methane emissions (Joblin, 1999). Unfortunately, till date the focus tends to be primarily on the amounts of methane produced rather than considering the disposal of H2 that impairs digestion and fermentation in the rumen if it stores.

Table 1: Methane abatement strategies, their mechanism and selection criteria

Formulations Mechanism Concerns References
Addition of starch rich diet Reduced ruminal pH, Induce greater proportion of propionate versus acetate  Risk of sub-acute ruminal acidosis (SARA) Hino and Hamano, (1993)
Addition of Lipids Biohydrogenation occur which inhibit methanogens and protozoa, Induce greater proportion of propionate versus acetate Long period studies required Czerkawski et al., 1966; Jordan et al., 2006b; Alexander et al., 2008
·         Fatty acids
·         Oils
·         Seeds
Defaunation Provide less hydrogen for methanogenesis Adaptation of microbiota may occur Abecia et al., 2012; Zhou et al., 2013;
· Chemical- Bromo-chloro-methane (BCM)
· Feed additives- Lauric acid
Methanogen Vaccine Enhance host immune response to methanogens Vaccine formulations and their targets Subharat et al., 2016
rGT2 Protein formulated with saponin
AdditionofIonophores  Inhibits protozoa and gram-positive bacteria Banned in the European Union Sauer et al., 1998
Addition of plant secondary metabolites Reduced hydrogen availability to methanogens Optimum dosage and long-term studies required Bodas et al., 2012
Addition of organic Acids Greater proportion of propionate, versus acetate Varies with diet Wood et al., 2009

However, a decline in methane production by 20-50% is known to be achievable without reducing feed intake and this should increase an energetic efficiency of digestion by 2-5%, and possibly more on high roughage diets (Tomkins and Hunter, 2003). Therefore, an understanding of the microorganisms and main metabolic pathways in the rumen is helpful in devising strategies to manage reducing equivalents flow in the rumen for decreased methanogenesis (Jeyanathan et al., 2014). In the rumen, methanogens assume the role of terminal reducers of carbon by using the hydrogen by-products generated from fungal, bacterial and protozoan energy. This process is called “inter species hydrogen transfer” and is important in maintaining the microbial fermentations and plant fiber degradation that occurs in the rumen by oxidizing and reusing reduced cofactors such as NADH. In rumen other than methanogens, the hydrogen evolved during microbial fermentation are utilized by a number of bacteria that act as alternate hydrogen sinker e.g. sulfate reducing bacteria, methylotrophs, propionate forming bacteria, nitrate/nitrite reducing bacteria, homoacetogens, and capnophiles. Among the different strategies studied, one promising option to produce less CH4 is using alternate hydrogen sinkers as direct fed microbial (DFM) for manipulation of biochemical pathways prevailing in the rumen. Direct fed microbial have been effectively used in rumen to prevent digestive disorders like acidosis and to reduce pathogenic load in young animals in such a way that they increase the overall productivity of ruminant system (Krehbiel et al., 2003; Adams et al., 2008; McAllister et al., 2011; Lettat et al., 2012b; Kalebich and Cardoso, 2018). They are recognized as the substitute to the use of antibiotics and chemical elements that may bring a risk of antibiotic resistance and residues in animal products. Though, to date there is little evidence to suggest the efficacy of DFM to control the production of CH4 in ruminants. Inside the rumen dominating community of methanogens consumes H2 to reduce CO2 to CH4. Some rumen methanogens can consume formate or methyl group containing compounds such as methanol and methylamine (Janssen and Kirs, 2008). Carbon dioxide constitutes up to 65% of total gas in the rumen and it is not a limiting substrate of rumen methanogenesis (Ellis et al., 1991). Therefore, H2 is a key compound for controlling CH4 production. The major biochemical pathways explored to decrease CH4 emissions from ruminants by using DFM are the redirection of H2 away from methanogenesis and decreased the production of H2 during feed fermentation are discussed below.

Propionate-Forming Bacteria

Type of diet given to animal affects the key volatile fatty acids (acetic, propionic, and butyric acid) produced in the rumen. The concentrate-based diet offered to ruminants results high propionate level as compared to high forage diet, which yields more acetate. Propionate formation consumes reducing equivalents (FADH2, NADH), where pyruvate is reduced to propionate, therefore it is considered as H2 -utilization pathway, while in H2 formation, protons (H+) are reduced to H2 (Baldwin et al., 1963). As H2 is the main precursor for CH4 production, increase in propionate formation was stoichiometrically associated with a decrease in CH4 production, as propionate biochemical pathway is majorly followed by bacterial DFM in ruminant production (Seo et al., 2010). The Propionibacterium species had been used as DFM in rumen to increase the animal productivity (Ghorbani et al., 2002; Adams et al., 2008). Further, Megasphaera elsdenii and Propionibacterium species were used to prevent rumen acidosis in concentrate-fed animals as well as Lactobacillus species have been used to reduce pathogenic counts in young animals. However, CH4 production status was not indicated in any of these studies (Aikman et al., 2011; Lettat et al., 2012b; McAllister et al., 2011). The decrease in CH4 emission was recently observed in lactating cows receiving a mixture of Propionibacterium jenseniiLactobacillus species. The DFM approach showed potential to mitigate rumen CH4 emission (Lettat et al., 2012a).

Nitrate/Nitrite-Reducing Bacteria

The metabolic pathway representing nitrate metabolism in the rumen is expected to be dissimilatory nitrate reduction in which nitrate is reduced to ammonia in two-step processes: nitrate to nitrite and nitrite to ammonia. The effective use of nitrate to reduce the rumen methanogenesis has been restricted due to toxicity of the nitrite. Rumen microbes quickly reduce the nitrate into nitrite, but the rate of reduction of nitrite into ammonia is slower, which can cause nitrite accumulation in the rumen (Iwamoto et al., 1999). Having the capability to reduce nitrate or nitrite, Wolinella succinogenes and Selenomonas ruminantium are required to be present at a concentration of 106 cells/ml of rumen fluid (Asanuma et al., 2002; Yoshii et al., 2003). The methanogens are prevailing in the rumen at the concentration of about 109 cells/ml, therefore to compete with them it may be useful to rise the activity of nitrate/ nitrite reducing bacteria in the rumen (Jeyanathan et al., 2011). Bacteria that have the ability to reduce nitrate or/and nitrite are more active when nitrate is included in the diet. In-vitro trials suggested that incorporation of nitrate increased the number of nitrate reducing bacteria such as Wolinella succinogenes and Veillonella parvula, but could not satisfactorily reduced methane production (Iwamoto et al., 2002). Therefore, providing nitrate/nitrite-reducing bacteria as DFM along with nitrate may improve the nitrate reduction process thereby avoid nitrite toxicity. Nitrate as feed additive can decrease rumen methanogenesis in different ruminant species and production conditions (Sophea et al., 2010; Van Zijderveld et al., 2011; Hulshof et al., 2012; Olijhoek et al., 2016). In rumen, during microbial protein synthesis, nitrate could replace urea as a nitrogen source in low nitrogen diets. In an in-vivo study replacement of 1.5% of urea by 3% calcium nitrate reduced CH4 emission (Li et al., 2012). However, the possible negative impact of long-term supplementation of nitrate on animal health has to be explored extensively.

Homoacetogens

Homoacetogens have been described in diverse environments including rumen, with the ability to produce acetate via heterotrophic and autotrophic growth. They propagate heterotrophically by utilizing sugars and autotrophically by utilizing formate, CO, and H2/CO2. Promotion of autotrophic growth of homoacetogens is thought to be a competitive pathway to methanogenesis as the same substrates are used. Acetate is a valuable nutrient for the host and for other microbes present inside the rumen. The total count of homoacetogens observed from rumen is inconstant (undetectable to 107 CFU/mL of rumen liquor) reliant on feed, age of the animal, and time of sampling (Fonty et al., 2007). Bearing in mind for preparation of acetogens as DFM, has some limitations such as tendency of methanogens to sequester H2 from rumen fermentation is more as compared to acetogens and it was found that energy yield from methanogenesis was greater than that of acetogenesis (Thauer et al., 1977). Studies have been reported where homoacetogens sustained efficient metabolisim inside the rumen and inhibited methanogenesis in absence of methanogens, to stimulate acetogenesis (Nollet et al., 1997; Fonty et al., 2007). However, the thermodynamic stability for acetogens in capturing the H2 from fermentation (28-46%) were comparatively less than methanogens (>90 %) which may affect the whole fermentation system in the rumen (Gagen et al., 2012). Latterly, Acetogenic bacterium was isolated from rumen, having ability to grow on low threshold concentrations of hydrogen (Boccazzi and Patterson, 2011). Such acetogens could participate with methanogens inside the rumen. Different studies have been accompanied in different environments (gut microbial ecosystem of humans, rodents, macropods, and wood-digesting termites) where homoacetogenesis demonstrated their active role in reducing methane emissions (Breznak and Switzer, 1986). The homoacetogen population observed in the forestomach of Tammar Wallaby (Macropus eugenii) was different when compared to the population found in ruminants, which could justified the reason for lowering of methane production (Gagen et al., 2010).

Capnophiles

The capnophiles require high levels of CO2 for their growth. The rumen is an anoxic chamber, where CO2 is one of its major gas. The occurrence of capnophiles in the rumen is therefore predictable but their use as scavengers of CO2 to mitigate methanogenesis remained doubtful as this gas is not a regulating factor for methanogenesis. Hypothesis has been given regarding two types of CO2 requirement among rumen bacteria: (a) Biosynthesis type, in which CO2 is required for cell growth e.g. Streptococcus bovis; (b) Bacteria that are forming succinate in addition to biosynthesis e.g. Succinivibrio dextrinosolvens, Mannheimia succiniciproducens, and Actinobacillus succinogenes (Dehority, 1971). During succinate production, CO2 is attached to the three-carbon phosphoenol pyruvate, an end product of glycolysis, to generate the four-carbon compound, oxaloacetate. The Oxaloacetate accepts two pair of electrons, when reduced into succinate. As such, both CO2 and H2 are used during this succinate formation and may have an impact on rumen methanogenesis. During the propionate production, succinate is also an important intermediate product. The Tammar Wallaby yields only one-fifth of the amount of CH4 produced by ruminants per unit of digestible energy intake (Kempton et al., 1976). A physiological difference such as shorter retention time of feed in the foregut partially describes this. The occurrence of a novel group of acetogenic bacteria may be the reason for the reduction in CH4 emission and the existence of capnophiles might be a potential contributor to this opinion (Gagen et al., 2010). The 16S rRNA clone library of capnophiles was analyzed from foregut samples of Tammar Wallaby and allocated to a group within the family Succinivibrionaceae. A member from this group was isolated and its genome sequence was analyzed, which proved that it was a capnophile, dependent on CO2 to support its metabolism by means of succinate biosynthesis (Pope et al., 2011). However, clear recognition of their metabolic pathway and analogous environmental conditions are needed to assess their potential as rumen CH4 mitigants.

Sulfate-Reducing Bacteria (SRB)

Sulfate reducing bacteria are obligate anaerobes which are present in diverse anaerobic enviornments like estuarine, saltmarsh and acidic sediments, landfills, freshwater lakes, sludge, and sewage drains (Andrea et al., 2015; Brand et al., 2015; Colin et al., 2017; Cui et al., 2017; Kashyap and Grover, 2017; Kharrat et al., 2017; Pimenov et al., 2014; Xia et al., 2014; Yang et al., 2017). Competitive relationships between methanogens and sulfate-reducing bacteria have been also described in the rumen (Paul et al., 2011). In anaerobic environments, sulfate reducing bacteria competes with methanogens for their conjoint substrates (formate, H2 and acetate). As the energy requirement of sulfate reduction was slightly more favorable (ΔG = -152 kJ/mol) than methanogenesis (ΔG = – 131 kJ/mol), encouraging competition between these two groups for common substrate i.e. hydrogen and thus, can decreases methanogenesis theoretically according to this process (Gibson et al., 1993). The synergestic association between methanogens and SRB is another illustration of interspecies H2 transfer. In sulfate-depleted environments syntrophic association of SRB and methanogens to generate and utilize H2 have been observed (Muyzer and Stams, 2008). The population of SRB in the rumen is small (105 to 106 CFU/mL of rumen liquor) and represents mainly the genus Desulfovibrio and Desulfotomaculum (Campbell and Postgate, 1965; Huisingh et al., 1974). Recently, a sulfate-reducing bacteria belonging to genus Fusobacterium have been isolated from buffalo suggesting that there might be other not-yet-cultured SRB in the rumen (Paul et al., 2011). Introduction of sulfate into the rumen can enhance the capability of SRB. As such, sulfate reduction might be facilitated by the introduction of SRB when sulfate was used as an additive to reduce methanogenesis (Cummings et al., 1995). Only limited studies have been done on the effect of sulfate supplementation in rumen methanogenesis (Morvan et al., 1996; Van Zijderveld et al., 2010). The toxic end product i.e. H2S resulting from the sulfate reduction might be the major reason for the lack of studies on this option. Using sulfate alone as an additive in animal diet cannot be an alternative for reduction of ruminal methanogenesis as can cause sulfide toxicity. Yet, SRB are flexible microorganisms and published information indicates that they might possess some characteristics favoring rumen CH4 mitigation. For instance, a decrease in CH4 emission was observed in an in-vitro study using the newly identified SRB, Fusobacterium species as a DFM with a high sulfate diet. After 3 days of incubation period methane production reduced from 2.66 to 1.64 mmol/g digested dry matter (DM) without accumulation of H2S (Paul et al., 2011). No accumulation of sulfide was reported in the previous study which might be due to its rapid consumption by other microbes such as cellulolytic bacteria for production of sulfur-containing amino acids or Fusobacterium species itself might be able to oxidize sulfide into sulfate as defined in the termite gut (Bryant, 1973; Droge et al., 2005).

Other Dietary Factors Affecting Methane Production

India possess the largest livestock production in the world i.e. of 520.6 million and ranked one in biggest number of cattle production that shares 16.1 % of world cattle population, buffaloes (57.9%), whereas second largest in number of goats (16.7%) and third largest in number of sheep (5.7%) (FAO, 2007). However, it undergoes a great challenge to provide feed both in a green and dry form required for increasing their number. There are several factors, which influence the methane production by the ruminants such as pH, volatile fatty acids, diet, levels and frequency of feeding, animal species, and environmental factors. The various factors responsible to affect the frequency of rumen to produce methane are mentioned below.

Dietary Components

Diet has a significant role on methanogens and methane production as both the quality and quantity of feed changes the efficiency of fermentation process. When a high concentration of carbohydrates diet are fed, a high quantity of methane emits, but highly digestible diet released low fraction of methane concentration (Johnson and Johnson, 1995). Diet comprising 30-40% concentrate exhibited 6-7% of gross energy (GE) intake whereas, diet comprising 80-90% concentrate exhibit only 2-3% of gross energy intake (Martin et al., 2010; Nampoothiri et al., 2018). It clearly shows that, increasing in concentration of concentrate in animal feed reduces the methane emissions. Forages carries complex carbohydrate components which comprises structural carbohydrates (digested by microorganisms) i.e. cellulose and hemicellulose and non-structural carbohydrates i.e. starch and sugars (digested by the enzymes). To minimize the methane emissions from rumen, energy-rich structural carbohydrates must be replaced with non-structural carbohydrates. This will results in upturn in feed intake, greater rates of ruminal fermentation and accelerated feed turnover. With help of starch-fermenting microbes, shift of VFA production will occur from acetate towards propionate metabolic pathway and due to decline in relative quantity of ruminal hydrogen sources it reduce the CH4 production (Kumar et al., 2013).

Plant Secondary Metabolites

Condensed tannins and saponins are significant ruminant feed additives due to its natural origin and can be used specifically for methane mitigation approach, as methane reduction capability has been recognized in both sources (Wanapat et al., 2013; Morales et al., 2018). There are two type of approaches that tannins can perform against methanogenesis i.e. direct and indirect influence on rumen methanogen and hydrogen production. It was also observed that after utilizing condensed tannin, not only it reduced methane level but also assisted amino acids to get absorbed in small intestine (Chanthakhoun et al., 2011). Saponins are basically natural occurring glycosides which can be found in many plants. Efficiency of feed utilization depends upon the quantity of protozoan population present in the rumen as their decreased quantity may improve the flow of microbial protein. In the interest of effective results, attention has been increasing in use of saponin-containing plants as a potential approach for suppressing or eliminating ruminal protozoa (Wanapat et al., 2013).

Organic Acids

To enhance nutritional requirement and their effect on methane reduction, use of organic acids have been investigated in animal feed (Morgavi et al., 2010; Kara et al., 2018). However carrying similar conditions varied and insufficient data has been recognized from in-vivo and in-vitro trial as no variations in methane reduction were observed in beef heifers when compared to beef cattle which showed 16% decreases in methane emission with supplementation of organic acids (Beauchemin et al., 2008; Foley et al., 2009). Unexpectedly, giant shift in CH4 reduction has been observed when encapsulated fumarate was used in the diet of lambs without any negative effect on animal growth. However, further research are needed to use such a product as additive (Wallace et al., 2006). It has been advised that the high malate content in early growth stage of fresh forages, especially lucerne, could lead to significant alterations in rumen microbial profile (Martin, 1998; Martin et al., 2010)

Lipids

Dietary fat could be a favorable nutritional substitute to lower ruminal methanogenesis without disturbing the ruminal parameters (Wanapat et al., 2013; Duthie et al., 2018). Lipid supplementation can lower the methane production either by reducing fiber digestion, lowering the dry matter intake, inhibiting the population of rumen protozoa via biohydrogenation, use of oils can provide a practical methodology to reducing methane in circumstances where animals can be given day-to-day feed supplements. However, surplus oil can be harmful to fiber digestion and animal production. Oils carrying medium chain fatty acids can act directly on methanogens and ciliate protozoans. Thus, using the mixture of coconut oil and garlic powder showed tendency to reduce methane and improving VFA profile (Kongmun et al., 2010). Many aspects need to be measured such as the form and type of oils well as its cost which has increased intensely in recent years due to their increased demand.

Conclusion

Looking at the evidences in a broad manner, profiling of rumen methanogens appears to be a significant tool for confirming the sustainability of ruminant-based agriculture production systems. Effective methane mitigation policies should be developed and adopted in such a way that systematic understanding of the microbial interaction of rumen methanogens can be understood. Approaches based on DNA analysis provide assistance in categorizing and exploring that how rumen microbes can influence rumen fermentation profile without affecting the animal’s production potential. Connecting the microbial profiles of animals to recognize the microbial shifts in rumen can be significant initiative among methane mitigation policies. Some of the dietary approaches used in different studies have made alterations in rumen microbial communities as exposed by profiling assays. The assessment of the rumen micro flora can be directly or indirectly interconnected to the methane mitigation policies for ruminants. In addition, advancement in genetic approaches and management practices for increasing ruminant productivity and abating methane emissions, in combination with other strategies, would provide new insights in reducing methane emission from ruminant system globally.

References

  1. Abecia, L., Toral, PG., Martin-Garcia, A. I., Martinez, G., Tomkins, NW., Molina-Alcaide, E., Newbold, CJ., and Yanez-Ruiz, DR. (2012). Effect of bromochloromethane on methane emission, rumen fermentation pattern, milk yield, and fatty acid profile in lactating dairy goats. Journal of Dairy Science 95, 2027-2036.
  2. Adams, M. C., Luo, J., Rayward, D., King, S., Gibson, R., and Moghaddam, GH. (2008). Selection of a novel direct-fed microbial to enhance weight gain in intensively reared calves. Animal Feed Science and Technology 145, 41-52.
  3. Aikman, P. C., Henning, PH., Humphries, DJ., and Horn, CH. (2011). Rumen pH and fermentation characteristics in dairy cows supplemented with Megasphaera elsdenii NCIMB 41125 in early lactation. Journal of Dairy Science 94, 2840-2849.
  4. ALGAS (1998). Asia Least-cost Greenhouse Gas Abatement Strategy, India. Asian Development Bank, Global Environment Facility, United Nations development Programme, Manila, The Philippines.
  5. Alexander, G., Singh. B., Sahoo, A., and Bhat, TK. (2008). In-vitro screening of plant extracts to enhance the efficiency of utilization of energy and nitrogen in ruminant diets. Animal Feed Science and Technology 145(1-4), 229-244.
  6. Andrea, IS., Stams, A. J. M., Hedrich, S., Nancucheo, I., and Johnson, DB. (2015). Desulfosporosinus acididurans nov.: an acidophilic sulfate reducing bacterium isolated from acidic sediments. Extremophiles 19(1), 39-47.
  7. Asanuma, N., Iwamoto, M., Kawato, M., and Hino, T. (2002). Numbers of nitrate reducing bacteria in the rumen as estimated by competitive polymerase chain reaction. Animal Science Journal 73, 199-205.
  8. Attwood, G., and McSweeney, C. (2008). Methanogen genomics to discover targets for methane mitigation technologies and options for alternative H2 utilization in the rumen. Australian Journal of Experimental Agriculture 48(2), 28-37.
  9. Balamurugan, B., Tejaswi, V., Priya, K., Sasikala, R., Karuthadurai, T., Ramamoorthy, M., and Jena, D. (2018). Effect of Global Warming on Livestock Production and Reproduction: An Overview. Research & Reviews: Journal of Veterinary Science and Technology 6(3), 12-18.
  10. Baldwin, R. L., Wood, WA., and Emery, RS. (1963). Conversion of glucose-C14 to propionate by the rumen microbiota. Journal of Bacteriology 85, 1346-1349.
  11. Beauchemin, K., Kreuzer, M., O’Mara, F., and McAllister, T. (2008). Nutritional management for enteric methane abatement: a review. Australian Journal of Experimental Agriculture 48, 21-27.
  12. Boccazzi, P., and Patterson, JA. (2011). Using hydrogen-limited anaerobic continuous culture to isolate low hydrogen threshhold ruminal acetogenic bacteria. Agriculture, Food and Analytical Bacteriology 1, 33-44.
  13. Bodas, R., Prieto, N., Garcia-Gonzalez, R., Andres, S., Giraldez, F. J., and Lopez, S. (2012) Manipulation of rumen fermentation and methane production with plant secondary metabolites. Animal Feed Science and Technology 176, 78-93.
  14. Brand, T. P. H., Roest, K., Chen, GH., Brdjanovic, D., and Loosdrecht, MCM. (2015). Occurrence and activity of sulfate reducing bacteria in aerobic activated sludge systems. World Journal of Microbiology and Biotechnology 31(3), 507-516.
  15. Breznak, J. A., and Switzer, JM. (1986). Acetate synthesis from H2 plus CO2 by termite gut microbes. Applied and Environmental Microbiology 52, 623-630.
  16. Bryant, MP. (1973). Nutritional requirements of the predominant rumen cellulolytic bacteria. Federation proceedings 32, 1809-1813.
  17. Bryant, M. P., Campbell, L. L., Reddy, CA., and Crabill, MR. (1977). Growth of Desulfovibrio in lactate or ethanol media low in sulfate in association with H2-utilizing methanogenic bacteria. Applied and Environmental Microbiology 33, 1162-1169.
  18. Campbell, L. L. and Postgate, JR. (1965). Classification of the spore-forming sulfate reducing bacteria. Bacteriological Reviews 29, 359-363.
  19. Chanthakhoun, V., Wanapat, M., Wachirapakorn, C., and Wanapat, S. (2011). Effect of legume (Phaseolus calcaratus) hay supplementation on rumen microorganisms, fermentation and nutrient digestibility in swamp buffalo. Livestock Science 140, 17-23.
  20. Chhabra, A., Manjunath, KR., Panigrahy, S., and Parihar, JS. (2013). Greenhouse gas emissions from Indian livestock. Climate Change 117, 329-344.
  21. Colin, Y., Urriza, M., Gassie, C., Carlier, E., Monperrus, M., and Guyoneaud, R. (2017). Distribution of sulfate reducing communities from estuarine to marine bay waters. Microbiology Ecology 73(1), 39-49.
  22. Czerkawski, J. W., Blaxter, KL., and Wainman, FW. (1966). The metabolism of oleic, linoleic and linolenic acids by sheep with reference to their effects on methane production. British Journal of Nutrition 20, 349-362.
  23. Cui, J., Chen, X., Nie, M., Fang, S., Tang, B., Quan, Z., Li, Bo., and Fang, C. (2017). Effects of Spartina alterniflora invasion on the abundance, diversity, and community structure of sulfate reducing bacteria along a successional gradient of costal salt marshes in China. Wetlands 37(2), 221-232.
  24. Cummings, B. A., Caldwell, DR., Gould, DH., and Hamar, DW. (1995). Rumen microbial alterations associated with sulfide generation in steers with dietary sulfate-induced polioencephalomalacia. American Journal of Veterinary Research 56, 1390-1395.
  25. Dehority, BA. (1971). Carbon dioxide requirement of various species of rumen bacteria. Journal of Bacteriology 105, 70-76.
  26. Dijkstra, J., Neal, H., Beever, D. E. and France, J. (1992). Simulation of nutrient digestion, absorption and outflow in the rumen: Model description. Journal of Nutrition 122, 2239-2256.
  27. Droge, S., Limper, U., Emtiazi, F., Schonig, I., Pavlus, N., Drzyzga, O., Fischer, U., and Konig, H. (2005). In-vitro and in-vivo sulphate reduction in the gut contents of the termite Mastotermes darwiniensis and the rose-chafer Pachnoda marginata. The Journal of General and Applied Microbiology 51, 57-64.
  28. Duthie, C. A., Troy, SM., Hyslop, J. J., Ross, DW., Roehe, R., and Rooke, JA. (2018). The effect of dietary addition of nitrate or increase in lipid concentrations, alone or in combination, on performance and methane emissions of beef cattle. Animal 12(2), 280-287.
  29. Ellis, J. E., McIntyre, PS., Saleh, M., Williams, A. G., and Lloyd, D. (1991). Influence of CO2 and low concentrations of O2 on fermentative metabolism of the ruminal ciliate Polyplastron multivesiculatum. Applied and Environmental Microbiology 57, 1400-1407.
  30. FAO (2007). Enteric fermentation 〈http://faostat3.fao.org/download/G1/GE/E〉 (accessed Feb2016).
  31. Foley, PA., Kenny, DA., Callan, J. J., Boland, TM., and O’Mara, FP. (2009). Effect of dl-malic acid supplementation on feed intake, methane emission and rumen fermentation in beef cattle. Journal of Animal Science 87, 1048-57.
  32. Fonty, G., and Joblin, KN. (1990). Rumen anaerobic fungi: their role and interactions with other rumen microorganisms in relation with fibre digestion. In: Tsuda T, Sasaki Y and Kawashima R (editors), Physiological aspects of digestion and metabolism in ruminants, Academic Press, San Diego, pp. 650-680.
  33. Fonty, G., Joblin, K., Chavarot, M., Roux, R., Naylor, G., and Michallon, F. (2007). Establishment and development of ruminal hydrogenotrophs in methanogen-free lambs. Applied and Environmental Microbiology 73, 6391-6403.
  34. Forabosco, F., Chitchyan, Z., and Mantovani, R. (2017) Methane, nitrous oxide emissions and mitigation strategies for livestock in developing countries: A review. South African Journal of Animal Science 47(3), 268-277.
  35. Gagen, E. J., Denman, S. E., Padmanabha, J., Zadbuke, S., Al Jassim, R., Morrison, M., and McSweeney, CS. (2010). Functional gene analysis suggests different acetogen populations in the bovine rumen and tammar wallaby forestomach. Applied and Environmental Microbiology 76, 7785-7795.
  36. Gagen, E. J., Mosoni, P., Denman, S. E., Al-Jassim, R., McSweeney, CS., and Forano, E. (2012). Methanogen colonisation does not significantly alter acetogen diversity in lambs isolated 17 h after birth and raised aseptically. Microbial Ecology 64, 628-640.
  37. Ghorbani, GR., Morgavi, D. P., Beauchemin, KA., and Leedle, JAZ. (2002). Effects of bacterial direct-fed microbials on ruminal fermentation, blood variables, and the microbial populations of feedlot cattle. Journal of Animal Science 80, 1977-1985.
  38. Gibson, GR., Macfariane, GT., and Cummings, JH. (1993). Sulphate reducing bacteria and hydrogen metabolism in the large intestine. Gut 34, 437-439.
  39. Hegarty, RS. (1999). Reducing rumen methane emissions through elimination of rumen protozoa. Australian Journal of Agricultural Research 50, 1321-1327.
  40. Hino, T., and Hamano, S. (1993). Effects of readily fermentable carbohydrate on fiber digestion by rumen microbes in continuous culture. Animal Science and Technology 64, 1070-1078.
  41. Hook, S. E., Wright, AD., and McBride, BW. (2010). Methanogens: methane producers of the rumen and mitigation strategies. Archaea doi:10.1155/2010/945785.
  42. Hristov, AN., Johnson, K. A., and Kebreab, E. (2014). Livestock methane emissions in the United States. Proceedings of the National Academy of Sciences 111(14), E1320. https://doi.org/10.1073/pnas.1401046111.
  43. Huisingh, J., McNeill, J. J., and Matrone, G. (1974). Sulfate reduction by a Desulfovibrio species isolated from sheep rumen. Applied Microbiology 28, 489-497.
  44. Hulshof, R. B. A., Berndt, A., Gerrits, WJJ., Dijkstra, J., Van Zijderveld, SM., Newbold, JR., and Perdok, HB. (2012). Dietary nitrate supplementation reduces methane emission in beef cattle fed sugarcane-based diets. Journal of Animal Science 90, 2317-2323.
  45. Hungate, RE. (1986) Rumen and its Microbes, Academic Press, Washington DC.
  46. Iwamoto, M., Asanuma, N., and Hino, T. (1999). Effect of nitrate combined with fumarate on methanogenesis, fermentation, and cellulose digestion by mixed ruminal microbes in-vitro. Animal Science Journal 70, 471-478.
  47. Iwamoto, M., Asanuma, N., and Hino, T. (2002). Ability of Selenomonas ruminantium, Veillonella parvula, and Wolinella succinogenes to reduce nitrate and nitrite with special reference to the suppression of ruminal methanogenesis. Anaerobe 8, 209-215.
  48. Janssen, PH., and Kirs, M. (2008). Structure of the archaeal community of the rumen. Applied and Environmental Microbiology 74, 3619-3625.
  49. Janssen, PH. (2010). Influence of hydrogen on rumen methane formation and fermentation balances through microbial growth kinetics and fermentation thermodynamics. Animal Feed Science and Technology 160(1-2), 1-22.
  50. Jeyanathan, J., Kirs, M., Ronimus, RS., Hoskin, SO., and Janssen, PH. (2011). Methanogen community structure in the rumens of farmed sheep, cattle and red deer fed different diets. Microbiology Ecology 76, 311-326.
  51. Jeyanathan, J., Martin, C., and Morgavi1, DP. (2014). The use of direct-fed microbials for mitigation of ruminant methane emissions: a review. Animal 8(2), 250-261.
  52. Joblin, KN. (1999). Ruminal acetogens and their potential to lower ruminant methane emissions. Australian Journal of Agricultural Research 50(8), 1307-1314.
  53. Johnson, K. A., and Johnson, DE. (1995). Methane emission from cattle. Journal of Animal Science 73, 2483-2492.
  54. Jordan, E., Lovett, DK., Monahan, F. J., Callan, J., Flynn, B., and O’Mara, FP. (2006b). Effect of refined coconut oil or copra meal on methane output and on intake and performance of beef heifers. Journal of Animal Science 84, 162-170.
  55. Kalebich, CC., and Cardoso, FC. (2018). Effects of Direct-Fed Microbials on Feed Intake, Milk Yield, Milk Composition, Feed Conversion, and Health Condition of Dairy Cows. In Nutrients in Dairy and their Implications on Health and Disease. pp. 111-121.
  56. Kamra, DN. (2005). Rumen microbial ecosystem. Current Science 89(1), 124-135.
  57. Kamra, DN., Saha, S., Bhatt, N., Chaudhary, L. C., and Agarwal, N. (2003). Effect of diet on enzyme profile, biochemical changes and in sacco degradability of feeds in the rumen of buffalo. Asian Australian Journal of Animal Sciences 16, 374-379.
  58. Kara, K., Ozkaya, S., Erbas, S., and Baytok, E. (2018). Effect of dietary formic acid on the in vitro ruminal fermentation parameters of barley-based concentrated mix feed of beef cattle. Journal of Applied Animal Research 46 (1), 178-183.
  59. Kashyap, V., and Grover, CR. (2017). Cultivation, isolation and identification of sulfate reducing bacteria employing Hungate technique. Octa Journal of Environmental Research 5(3), 206-213.
  60. Kempton, T. J., Murray, RM., and Leng, RA. (1976). Methane production and digestibility measurements in grey-Kangaroo and sheep. Australian Journal of Biological Sciences 29, 209-214.
  61. Kharrat, H., Karry, F., Bartoli, M., Hnia, W., Mhiri, N., Fardeau, M., Bennour, F., Kamoun, L.N., Alazard, D., and Sayadi, S. (2017). Desulfobulbus aggregans nov, a novel sulfate reducing bacterium isolated from marine sediments from Gulf of Gabes. Current Microbiology 74(4), 449-454.
  62. Knapp, JR., Laur, GL., Vadas, PA., Weiss, W. P., and Tricarico, JM. (2014). Enteric methane in dairy cattle production: Quantifying the opportunities and impact of reducing emissions. Journal of Dairy Science 97, 3231-3261.
  63. Kongmun, P., Wanapat, M., Pakdee, P., and Navanukraw, C. (2010). Effect of coconut oil and garlic powder on in-vitro fermentation using gas production technique. Livestock Science 127, 38-44.
  64. Krehbiel, CR., Rust, SR., Zhang, G., and Gilliland, SE. (2003). Bacterial direct-fed microbials in ruminant diets: performance response and mode of action. Journal of Animal Science 81, 120-132.
  65. Kumar, S., Dagar, SS., Sirohi, SK., Upadhyay, R. C., and Puniya, AK. (2013). Microbial profiles, in-vitro gas production and dry matter digestibility based on various ratios of roughage to concentrate. Annals of Microbiology 63, 541-545.
  66. Kumari, S., Hiloidhari, M., Kumari, N., Naik, S. N., and Dahiya, RP. (2018) Climate change impact of livestock CH4 emission in India: Global temperature change potential (GTP) and surface temperature response. Ecotoxicology and Environmental Safety 147, 516-522.
  67. Leng, L., Zhong, X., Zhu, R. J., Yang, SL., Gou, X., and Mao, HM. (2011). Assessment of protozoa in Yunnan Yellow cattle rumen based on the 18S rRNA sequences. Molecular Biology Reports 38(1), 577-585.
  68. Lettat, A., Noziere, P., Berger, C., and Martin, C. (2012a). Method for reducing methane production in a ruminant animal. In World Intellectual Property Organization. http://www.sumobrain.com/patents/wipo/wo2012147044.html.
  69. Lettat, A., Noziere, P., Silberberg, M., Morgavi, D. P., Berger, C., and Martin, C. (2012b). Rumen microbial and fermentation characteristics are affected differently by bacterial probiotic supplementation during induced lactic and subacute acidosis in sheep. Bio Med Central, Microbiology 12, 142-154.
  70. Li, L., Davis, J., Nolan, J., and Hegarty, R. (2012). An initial investigation on rumen fermentation pattern and methane emission of sheep offered diets containing urea or nitrate as the nitrogen source. Animal Production Science 52, 653-658.
  71. Liu, Y., and Whitman, WB. (2008). Metabolic, phylogenetic, and ecological diversity of the methanogenic archaea. Annals of the New York Academy of Sciences 1125, 171-189.
  72. Martin, C., Morgavi, D. P., and Doreau, M. (2010). Methane mitigation in ruminants: from microbe to the farm scale. Animal 4, 351-365.
  73. Martin, SA. (1998). Manipulation of ruminal fermentation with organic acids: a review. Journal of Animal Science 76, 3123-3132.
  74. McAllister, T. A., and Newbold, CJ. (2008). Redirecting rumen fermentation to reduce methanogenesis. Australian Journal of Experimental Agriculture 48, 7-13.
  75. McAllister, T. A., Beauchemin, KA., Alazzeh, AY., Baah, J., Teather, RM., and Stanford, K. (2011). Review: the use of direct fed microbials to mitigate pathogens and enhance production in cattle. Canadian Journal of Animal Science 91, 193-211.
  76. Miller, ME., Yeoman, CJ., Chia, N., Tringe, SG., Angly, FE., Edwards, RA., Flint, HJ., Lamed, R., Bayer, EA., and White, BA. (2012). Phage-bacteria relationships and CRISPR elements revealed by a metagenomic survey of the rumen microbiome. Environmental Microbiology 14(1), 207-27.
  77. Mitsumori, M., and Sun, W. (2008). Control of rumen microbial fermentation for mitigating methane emissions from the rumen. Asian-Australasian Journal of Animal Sciences 21(1), 144-154.
  78. Morales, E. R., Rossi, G., Cattin, M., Jones, E., Braganca, R., and Newbold, CJ. (2018). The effect of an isoflavonid-rich liquorice extract on fermentation, methanogenesis and the microbiome in the rumen simulation technique. FEMS Microbiology Ecology 94(3). https://doi.org/10.1093/femsec/fiy009.
  79. Morgavi, D. P., Forano, E., Martin, C., and Newbold, CJ. (2010). Microbial ecosystem and methanogenesis in ruminants. Animal 4(7), 1024-1036.
  80. Morvan, B., RieuLesme, F., Fonty, G., and Gouet, P. (1996). In-vitro interactions between rumen H2-producing cellulolytic microorganisms and H2-utilizing acetogenic and sulfate-reducing bacteria. Anaerobe 2, 175-180.
  81. Muyzer, G., and Stams, AJM. (2008). The ecology and biotechnology of sulphate-reducing bacteria. Nature Reviews Microbiology 6, 441-454.
  82. Nampoothiria, V. M., Mohini, M., Malla, BA., Mondal, G., and Pandit, S. (2018). Growth performance, and enteric and manure greenhouse gas emissions from Murrah calves fed diets with different forage to concentrate ratios. Animal Nutrition. https://doi.org/10.1016/j.aninu.2018.01.009.
  83. Nathani, N. M., Patel, A. K., Dhamannapatil, PS., Kothari, RK., Singh, KM., and Joshi, CG. (2013). Comparative evaluation of rumen metagenome community using qPCR and MG-RAST. AMB Express 3, 55.
  84. Newbold, C. J., Fuente, G. D. L., Belanche, A., Morales, ER., and McEwan, NR. (2015). The Role of Ciliate Protozoa in the Rumen. Frontiers in Microbiology 6, 1313.
  85. Nollet, L., Demeyer, D., and Verstraete, W. (1997). Effect of 2-bromoethanesulfonic acid and Peptostreptococcus productus ATCC 35244 addition on stimulation of reductive acetogenesis in the ruminal ecosystem by selective inhibition of methanogenesis. Applied and Environmental Microbiology 63, 194-200.
  86. Odenyo, A. A., Mackie, R. I., Stahl, DA., and White, BA. (1994). The Use of 16S rRNA-targeted oligonucleotide probes to study competition between ruminal fibrolytic bacteria: Development of probes for Ruminococcus species and evidence for bacteriocin production. Applied and Environmental Microbiology 60(10), 3688-3696.
  87. Olijhoek, D. W., Hellwing, ALF, Brask, M., Weisbjerg, MR., Hoberg, O., Larsen, MK., Dijkstra, J., Erlandsen, EJ., and Lund, P. (2016). Effect of dietary nitrate level on enteric methane production, hydrogen emission, rumen fermentation, and nutrient digestibility in dairy cows. Journal of Dairy Science 99(8), 6191-6205.
  88. Pathak, H., Upadhyay, R. C., Muralidhar, M., Bhattacharyya, P., and Venkateswarlu, B. (Eds.) (2013). Measurement of Greenhouse Gas Emission from Crop, Livestock and Aquaculture, Indian Agricultural Research Institute, New Delhi, pp.101.
  89. Patra, AK. (2012). Enteric methane mitigation technologies for ruminant livestock: a synthesis of current research and future directions. Environmental Monitoring and Assessment 184, 1929-1952.
  90. Patra, AK. (2014). Trends and Projected Estimates of GHG Emissions from Indian Livestock in Comparisons with GHG Emissions from World and Developing Countries. Asian-Australas Journal of Animal Science 27(4), 592-599.
  91. Paul, SS., Deb, SM., and Singh, D. (2011) Isolation and characterization of novel sulphate-reducing Fusobacterium and their effects on in-vitro methane emission and digestion of wheat straw by rumen fluid from Indian riverine buffaloes. Animal Feed Science and Technology 166-167, 132-140.
  92. Paul, SS., Kamra, DN., Sastry, V. R. B., Sahu, NP., and Kumar, A. (2003). Effect of phenolic monomers on growth and hydrolytic enzyme activities of an anaerobic fungus isolated from wild Nilgai (Boselaphus tragocamelus). Letters in Applied Microbiology 36, 377-381.
  93. Pimenov, NV., Zakharova, EE., Bryukhanov AL., Korneeva, VA., Kuznetsov, BB., Tourova, TP., Pogodaeva, TV., Kalmychkov, GV., and Zemskaya, TI. (2014). Activity and structure of the sulfate-reducing bacterial community in the sediments of the southern part of lake Baikal. Microbiology 83(1-2), 47-55.
  94. Pope, PB., Smith, W., Denman, SE., Tringe, SG., Barry, K., Hugenholtz, P., McSweeney, CS., McHardy, AC., and Morrison, M. (2011). Isolation of Succinivibrionaceae implicated in low methane emissions from Tammar wallabies. Science 333, 646-648.
  95. Russell, JB., and Rychlik, JL. (2001). Factors that alter rumen microbial ecology. Science 292, 1119-1122.
  96. Sahu, N. P., Kamra, DN., and Paul, SS. (2004). Effect of cellulose degrading bacteria isolated from wild and domestic ruminants on in-vitro digestibility of feed and enzyme production. Asian-Australasian Journal of Animal Sciences 17, 199-202.
  97. Santra, A., Kamra, DN., and Pathak, NN. (1995). Influence of ciliate protozoa on biochemical changes and hydrolytic enzymes in the rumen of buffalo (Bubalus bubalis). Buffalo Journal 12, 95-100.
  98. Sauer, F. D., Fellner, V., Kinsman, R., Kramer, JKG., Jackson, HA., Lee, AJ., and Chen, S. (1998). Methane output and lactation response in Holstein cattle with monensin or unsaturated fat added to the diet. Journal of Animal Science 76, 906-914.
  99. Seo, J. K., Kim, SW., Kim, M. H., Upadhaya, SD., Kam, DK., and Ha, JK. (2010). Direct-fed microbials for ruminant animals. Asian-Australasian Journal of Animal Science 23, 1657-1667.
  100. Singh, S., Kushwaha, BP., Nag, SK., Bhattacharya, S., Gupta, PK., Mishra, A. K., and Singh, A. (2012). Assessment of enteric methane emission of Indian lives tock in different agro-ecological regions. Current Science 102, 1017-1027.
  101. Singhal, K. K., Mohini, M., Jha, A. K., and Gupta, PK. (2005). Methane emission estimates from enteric fermentation in Indian livestock: Dry matter intake approach. Current Science 88(1), 119-127.
  102. Sirohi, SK., Singh, N., Dagar, SS., and Puniya, AK. (2012). Molecular tools for deciphering the microbial community structure and diversity in rumen ecosystem. Applied Microbiology and Biotechnology 95(5), 1135-1154.
  103. Sophea, IV., Khieu, B., Leng,​ , and Pr​​eston​ TR.​​ (2010). Effect of different levels of supplementary potassium nitrate replacing urea on growth rates and methane production in goats fed sugar palm-soaked rice straw and mimosa foliage. MSc Thesis, MEKARN-SLU. http://www.mekarn.org/MSC2008-10/theses/sophea.htm
  104. Subharat, S., Shu, D., Zheng, T., Buddle, BM., Kaneko, K., Hook, S., Janssen, PH., and Wedlock, (2016). Vaccination of sheep with a methanogen protein provides insight into levels of antibody in saliva needed to target ruminal methanogens. PLoS One 11(7), e0159861
  105. Swamy, M., and Bhattacharya, S. (2006). Budgeting anthropogenic greenhouse gas emission from Indian livestock using country-specific emission coefficients. Current Science 91, 1340-1353.
  106. Thauer, R. K., Jungermann, K., and Decker, K. (1977). Energy-conservation in chemotropic anaerobic bacteria. Bacteriological Reviews 41, 100-180.
  107. Tomkins, N. W., and Hunter, RA. (2003). Methane mitigation in beef cattle using a patented anti-methanogen. In: Eckard, R. & Slattery, B. (Eds). Proceedings of the 2nd Joint Australia and New Zealand Forum on Non-CO2 Greenhouse Gas Emissions from Agriculture, Lancemore Hill, Kilmore, Va, 20-21. Canberra, Australia, Cooperative Research Centre for Greenhouse Accounting, p. F3.
  108. USEPA (2014). Emission Factors for Greenhouse Gas Inventories. Washington D.C., USA.
  109. Van Zijderveld, SM., Gerrits, W. J. J., Dijkstra, J., Newbold, JR., Hulshof, RBA., and Perdok, HB. (2011). Persistency of methane mitigation by dietary nitrate supplementation in dairy cows. Journal of Dairy Science 94, 4028-4038.
  110. Van Zijderveld, SM., Gerrits, W. J. J., Apajalahti, JA., Newbold, JR., Dijkstra, J., Leng, RA., and Perdok, HB. (2010). Nitrate and sulfate: effective alternative hydrogen sinks for mitigation of ruminal methane production in sheep. Journal of Dairy Science 93, 5856-5866.
  111. Wallace, R. J., Wood, TA., Rowe, A., Price, J., Yanez, DR., and Williams, SP. (2006). Encapsulated fumaric acid as a means of decreasing ruminal methane emissions. Elsevier International CongressSeries1293.In: Soliva CR, Takahashi J, Kreuzer M editors. Greenhouse gases and animal agriculture: an update. Amsterdam, The Netherlands:Elsevier.pp. 48-51
  112. Wanapat, M., Kang, S., and Polyorach, S. (2013). Development of feeding systems and strategies of supplementation to enhance rumen fermentation and ruminant production in the tropics. Journal of Animal Science and Biotechnology 4, 32.
  113. Williams, A. G., and Coleman, GS. (1985). Hemicellulose degrading enzymes in rumen ciliate protozoa. Current Microbiology 12, 85-90.
  114. Wolin, M., Miller, T., and Stewart, C. (1997). Microbe-microbe interactions. In the rumen microbial ecosystem (ed. P Hobson and C Stewart), Chapman and Hall, London. pp. 467-491.
  115. Wood, T.,Wallace, R., Rowe, A., Price, J., Yanez-Ruiz, D., Murray, P., and Newbold, C. (2009). Encapsulated fumaric acid as a feed ingredient to decrease ruminal methane emissions. Animal Feed Science and Technology 152, 62-71
  116. Xia, FF., Su, Y., Wei, X. M., He, Y. H., Wu, ZC., Ghulam, A., and He, R. (2014). Diversity and activity of sulfur-oxidizing bacteria and sulfate-reducing bacteria in landfill cover soils. Letters in Applied Microbiology 59(1), 26-34.
  117. Yamaji, K., Ohara, T., and Akimoto, H. (2003). A country- specific, high-resolution emission inventory for methane from livestock in Asia in 2000. Atmospheric Environment 37, 4393-4406.
  118. Yang, K., Zhu, Y., Shan, R., Shao, Y., and Tian, C. (2017). Heavy metals in sludge during anaerobic sanitary landfill: speciation transformation and phytotoxicity. Journal of Environmental Management 189, 58-66.
  119. Yoshii, T., Asanuma, N., and Hino, T. (2003). Number of nitrate- and nitrite-reducing Selenomonas ruminantium in the rumen, and possible factors affecting its growth. Animal Science Journal 74, 483-491.
  120. Zhou, X., Meile, L., Kreuzer, M., and Zeitz, JO. (2013). The effect of lauric acid on methane production and cell viability of Methanobrevibacter ruminantium. Advances in Animal Biosciences 4(2), 458.
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