ReviewMethane production and estimation from livestock husbandry: A mechanistic understanding and emerging mitigation options
Graphical abstract
Introduction
The ruminant husbandry or livestock sector is experiencing rapid changes structurally and functionally with the increasing rate of human population and demands for livestock products. Globally, the per capita consumption of livestock products has become doubled in the past few decades (Herrero et al., 2016). In the last decades, milk supply and demand has increased by 26% and 2.4% annually and will rise by 25% in the coming years (Matthews et al., 2019). Livestock contributed about $1.4 trillion to the global asset (Thronton, 2010), equal to 50% of the total economy of the agricultural sector (Herrero et al., 2016).
Livestock contributed about 7.1 gigatonnes CO2e y−1 to the global anthropogenic GHGs emissions, equivalent to 14.5% of total GHGs emissions (Gerber et al., 2013). Approximately 44% of global livestock emissions occur in the form of methane (CH4) (Matthews et al., 2019). China, India, Brazil, USA, and Pakistan are the top five livestock farming countries, and together, they contribute 46% of global livestock-mediated anthropogenic GHGs emissions (FAO, 2012). The periodic trend of livestock CH4 emissions from 1961 to 2017 for the top five emitters is shown in Fig. 1. The enteric CH4 emission showed increasing trends for all the countries but started declining in the USA after 1975, and in China after 1980. The CH4 emission from the manure management also showed an increasing trend for all the countries except the USA. The global distribution of total GHGs (N2O and CH4) emissions from livestock is represented in. Fig. S1.
CH4 is the second most important anthropogenic GHGs in terms of global warming potential (GWP) with an estimated increase of 0.3% in 2016 to a total of 9.2 Gt CO2 eq (Olivier et al., 2017). Normally, CH4 is produced by the methanogens, in the rumens of an animal during the fermentation of feeds (Swamy and Bhattacharya, 2006; Kumari et al., 2014; McAuliffe et al., 2015). CH4 is also produced and emitted from the animal manures (McAuliffe et al., 2015). These two processes contributed about 100 and 9.9 Tg y−1 to global CH4 emissions, respectively (FAOSTAT, 2019). The enteric fermentation process contributes >90% CH4 emissions from livestock (FAO, 2012; Singh et al., 2012; Havlik et al., 2011).
The scientific community is confronted with the challenge of developing sustainable technical approaches to reduce CH4 emissions without compromising the demand for livestock products and its economic benefits. It will require a complete understanding of the enteric CH4 production, emission, measurement techniques, and mitigation measures. We reviewed the available literature related to various CH4 measurement techniques and mitigation approaches for the livestock sector.
Section snippets
Ruminants and CH4 production
CH4 is mainly produced in the rumen (multi-chambered stomach) of the ruminants (cattle, deer, camels) during the microbial fermentation of the animal feeds, particularly complex carbohydrate, i.e. polysaccharides (McSweeney and Mackie, 2012; Albrao et al., 2014). The ruminant stomach is composed of four pregastric fermentation chambers (rumen, reticulum, omasum, and abomasum). Various portions of the digestive tract, molecule received, enzymes released, and molecule produced are mentioned in
Microbial ruminant ecosystem and microbial diversity
Microbial ruminant ecosystem (MRE) has an anaerobic environment with high microbial population density (Lozano et al., 2017). Environmental conditions such as pH (5.5–7), temperature (38–42 °C), redox potential (250 to 450 mV) controlled by buffer present in saliva of ruminant and osmolarity (260–340 mOsm) are well suited to the growth of different microbial population to digest the plant materials in livestock rumen (Valente et al., 2016). The composition of the microbial populations
Methane emissions estimation techniques
To reduce GHGs emissions from livestock, reliable CH4 estimation and mitigation techniques are required (Hyland et al., 2016). GHGs emissions estimation can be done either through top-down or bottom-up approaches (Table 1). The bottom-up approach is based on emission inventories, while the top-down approach is based on inverse modeling (Schneising et al., 2014). Inverse modeling techniques are based on independent information from atmospheric measurements, i.e. satellite data with the
CH4 emissions mitigation strategies
The opportunities of CH4 emissions mitigation from livestock fall into three categories (i) reducing emission that involves the detailed understanding of their effect on factors such as production costs, competitiveness and risks incurred by stakeholders along the supply chain (Gerber et al., 2013), (ii) enhancing removals and (iii) avoiding emission. Reducing CH4 emission strategies targeted on emission reduction by the following ways (i) dietary manipulation, (ii) breeding management, and
Conclusion and recommendations
Livestock farming or ruminant husbandry is a significant source of livelihood and economy. It is also a major component of the diet in human food. Livestock farming is responsible for a major amount of GHGs emissions. Livestock farming should be practiced with minimal GHG emissions without reducing productivity. We discussed various mitigation options namely dietary management, breeding and other livestock management, which has the potential to mitigate CH4 emissions. The adoption of these
Acknowledgment
Dr. S. Kumari is thankful to the University Grants Commission, Government of India for Senior Research Fellowship (18-12/2011(ii)EUV/202236).
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