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. 2023 Jan;107(1):37-52.
doi: 10.1111/jpn.13696. Epub 2022 Mar 5.

Effects of incremental increases in grass silage proportions from different harvest years on methane emissions, urinary nitrogen losses, and protein and energy utilisation in dairy cows

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Effects of incremental increases in grass silage proportions from different harvest years on methane emissions, urinary nitrogen losses, and protein and energy utilisation in dairy cows

Amy Birkinshaw et al. J Anim Physiol Anim Nutr (Berl). 2023 Jan.

Abstract

Dairy cows, methane and global warming have become publicly related terms. However, appropriate dairy cow management may in fact be part of the climate solution when viewed as part of the biogenic carbon cycle. Accordingly, governments and consumers are encouraging more sustainable, locally produced, climate friendly dairy production that often includes grassland-based feeding. However, this system is presumed to result in greater methane emissions compared to corn silage- or concentrate-based diets. An increase in urine nitrogen, associated with increased ammonia and nitrous oxide emission potential, questions the environmental usefulness of this strategy pertaining to global warming. This study is the first to compare the effects of incremental increases of grass silage proportion on enteric methane production as well as N and energy losses in dairy cows. Twenty-four mid- to end-lactation dairy cows were each fed one of 24 different diets, from two different harvest years, gradually increasing in grassland-based feeds (grass silage and hay) from about 500 to 1000 g/kg and concomitantly decreasing in corn silage. Each cow underwent a 7-day total collection period and was housed for 48 h in respiration chambers. Incremental data were subjected to an approved parametric regression analysis approach. The dietary increase in grassland-based feeds did not impair milk yield, N and energy utilisation. Simplified regression equations revealed that, contrary to current assumptions, there was a decline in methane production from 373 to 303 g/day when increasing grassland-based feeds from 500 to 1000 g/kg diet, and there was a trend for a decline in emission intensity from 20.6 to 17.6 g/kg of energy-corrected milk. However, urine nitrogen emissions clearly increased even when related to nitrogen intake; the latter from 260 to 364 g/kg when increasing grassland-based feeds from 500 to 1000 g/kg. Methane and urine nitrogen emissions were not affected by year of harvest.

Keywords: ammonia; cattle; grassland-based feed; methanogenesis; nitrogen; protein.

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Conflict of interest statement

The authors declare no conflict of interest.

Figures

Figure 1
Figure 1
(a) Dry matter intake (DMI) relative to metabolic body weight (BW0.75), (b) energy‐corrected milk (ECM), (c) feed conversion efficiency, (d) milk urea content, and (e) urinary‐N to milk N ratio with increasing dietary grass silage proportions (for regression equations and coefficients see Table 6). p‐values of the equations are presented in the legend
Figure 2
Figure 2
Methane emissions (a: absolute; b: per dry matter intake [DMI]; c: per digestible organic matter [OM]; d: per digestible neutral detergent fibre [NDF]; e: per energy‐corrected milk [ECM]; f: per gross energy [GE] = Ym) with increasing dietary grass silage proportions (for regression equations and coefficients see Table 6). p‐values of the equations are presented in the legend
Figure 3
Figure 3
Energy loss (a) and turnover (b) as well as nitrogen (N) loss (c) and turnover (d) with increasing dietary grass silage proportions (for regression equations and coefficients see Table 6). p‐values of the equations are presented in the legend

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References

    1. AOAC International . (1995). Official methods of analysis. Association of Official Analytical Chemists.
    1. Beauchemin, K. A. , Kreuzer, M. , O'Mara, F. , & McAllister, T. A. (2008). Nutritional management for enteric methane abatement: A review. Australian Journal of Experimental Agriculture, 48, 21–27. 10.1071/EA07199 - DOI
    1. Beauchemin, K. A. , Ungerfeld, E. M. , Eckard, R. J. , & Wang, M. (2020). Fifty years of research on rumen methanogenesis: Lessons learned and future challenges for mitigation. Animal, 14(S1), S2–S16. 10.1017/S1751731119003100 - DOI - PubMed
    1. Boadi, D. , Benchaar, C. , Chiquette, J. , & Massé, D. (2004). Mitigation strategies to reduce enteric methane emissions from dairy cows: Update review. Canadian Journal of Animal Science, 84, 319–335. 10.4141/A03-109 - DOI
    1. Brouwer, E. (1965). Report of sub‐committee on constants and factors. In Blaxter K. L. (Ed.), Energy metabolism of farm animals: Third symposium on energy metabolism, EAAP Publ, 11 (pp. 441–443). Academic Press.