Elsevier

Small Ruminant Research

Volume 161, April 2018, Pages 28-33
Small Ruminant Research

Methane emissions and productivity of defaunated and refaunated sheep while grazing

https://doi.org/10.1016/j.smallrumres.2018.02.004Get rights and content

Highlights

  • Defaunated sheep displayed a decreased proportion of acetate and increased proportion of butyrate in ruminal VFA.

  • Methane yield tended to be lower in defaunated than refaunated sheep while grazing.

  • Liveweight gain and wool production were not different between defaunated and refaunated sheep.

Abstract

Rumen protozoa produce hydrogen, which can be utilised by methanogens to produce enteric methane (CH4) that is a loss of digested energy and has an adverse environmental impact as a greenhouse gas. The aim of this study was to examine the effect of the absence of rumen protozoa on pasture intake, ruminal fermentation and enteric CH4 production and performance of grazing sheep. An incomplete crossover experiment was conducted with eleven crossbred ewes (6 without [defaunated] and 5 with protozoa [refaunated]) on 2 × 2 ha pastures with daily CH4 production (DMP) being measured by GreenFeed Emission Monitoring (GEM) units. Grazing defaunated sheep exhibited a lower concentration of rumen ammonia (P = 0.01), but similar concentrations of total rumen volatile fatty acids compared to refaunated sheep (P > 0.05). The molar proportion of acetate was decreased and butyrate proportion was increased by defaunation, while the proportion of propionate was unchanged. Estimated pasture intake was not different between defaunated and refaunated sheep (P > 0.05). Defaunated sheep tended to have a higher total dry matter intake (tDMI; P = 0.06), being the sum of pasture intake and pellet supplement intake. There was a tendency towards a lower CH4 yield (g CH4/kg tDMI; P = 0.07) in defaunated sheep, but no differences in average daily gain or wool growth occurred due to defaunation.

Introduction

The requirement to produce at least 70% more food in order to feed 9 billion people by 2050 (World Bank, 2008; Bijl et al., 2017) is a major challenge to animal production. The livestock population has surged in many developing countries in response to this rapid growing demand for livestock products and is forecast to rise further (FAO, 2006; Herrero et al., 2014). In association with an increased global human demand for food, an increased livestock products result in increased greenhouse gas (GHG) emissions which are expected to increase in coming years (van Beek et al., 2010). Recent meta-analysis confirms that removal of ciliate protozoa from the rumen of ruminants can increase livestock average daily gain (ADG) by 9% and reduce enteric methane (CH4) emissions by 11% (Newbold et al., 2015). The positive effect of defaunation on animal growth is often seen with poor quality roughage diets that are low in nitrogen content and provide insufficient rumen degradable protein for the growth of rumen microbes (Bird and Leng 1978; William and Coleman, 1992). This may be advantageous in the tropics where forages are often deficient in protein and have higher fibre content than do temperate grasses (Minson, 1990). Since higher fibre content is associated with a great CH4 yield (g CH4/kg DMI; Margan et al., 1988; Pelchen and Peters 1998), a greater CH4 yield as well as reduced animal performance can be expected to coincide if dietary fibre content increases. This suggests that elimination of rumen protozoa can improve growth and reduce CH4 emissions of ruminants grazing on tropical or other low quality forages. However, there is little data from grazing animals available (Bird and Leng, 1984, Hegarty et al., 2000) and no grazing CH4 production data. This study was conducted to quantify whether effects of defaunation on volatile fatty acid, intake, wool growth and CH4 production observed in controlled feeding studies are also evident in grazing environments.

Section snippets

Animals and experimental procedures

The animals and defaunation treatments were described previously (Nguyen et al., 2016). Briefly, twelve crossbred ewes (Border Leicester rams × Merino ewes) about 30 months of age, were defaunated by treatment with sodium 1-(2-sulfonatooxyethoxy) dodecane (Empicol ESB/70AV, Albright and Wilson Australia Ltd, Melbourne) administered at 10 g/day in a 10% v/v solution for three consecutive days. After defaunation one sheep was slow to recover appetite, so was removed from the study. Eighteen weeks

Pastures

The availability of pGDM and pDDM and quality parameters of total DM are shown in Table 2. The paddocks did not differ in dead biomass availability (P > 0.05), but the pGDM tended to increase in biomass from period 1 to period 2 (P = 0.08). The chemical composition of pastures in the paddocks was different (P < 0.05) and was affected by period. Pasture NDF (P = 0.06) and ADF (P = 0.06) tended to increase between period 1 (67.03% and 42.25%, respectively) and period 2 (70.83% and 44.60%,

Animal productivity

While pDMI and DMD were not measured directly in this study; pDMI was estimated by GrazFeed and DMD by Si concentration in pasture and faecal DM and no protozoa effects on these were observed. Lower DMI and DMD in defaunated ruminants are often reported in the literature (Newbold et al., 2015), probably due to the loss of protozoal fibrolytic activity and longer particle retention time in the rumen associated with the slower rumen outflow and greater rumen fill resulting from lower ruminal DMD (

Conclusion

This study reported for the first time that MY tended to be lower in protozoa-free sheep relative to refaunated sheep in the grazing environment; an accurate measure of pasture intake, therefore, is required to confirm this finding. The lack of animal performance (ADG and CWG) responses to defaunation, together with lack of effect on DMP suggest the need for caution in assuming defaunation will improve the productivity and reduce the environmental impact of grazing ruminants.

Conflict of interest

We wish to confirm that there are no known conflicts of interest.

Acknowledgements

This research was funded by Meat and Livestock Australia and the Australian Government Department of Agriculture through the “Filling the Research Gap Program”. The authors are grateful for the assistance of Mr Derek Schneider for assessment of pasture green dry matter on offer using a Crop Circle™ ACS 210.

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