Publication | Open Access
Ammonia and methane emissions from small herd cattle buildings in a cold climate
15
Citations
45
References
2023
Year
Ammonia (NH<sub>3</sub>) and methane (CH<sub>4</sub>) emission measurements that reflect local production conditions are required to track progress in national emission policies and verify emission factors. The findings can also be used to better understand key factors influencing emissions. This is especially important in Norway, which has long cold winters, and small cattle herds in mechanically ventilated buildings. However, until now, NH<sub>3</sub> and CH<sub>4</sub> emissions from Norwegian cattle buildings have not been reported in literature. Moreover, in other cold climates, NH<sub>3</sub> and CH<sub>4</sub> emissions are often taken from large dairy herds in naturally ventilated buildings, with less focus on suckler cows. The objectives were to assess indoor climate, report NH<sub>3</sub> and CH<sub>4</sub> emissions and examine the impact of climatic factors on NH<sub>3</sub> and CH<sub>4</sub> emissions in three small herd dairy and suckler cow buildings over three seasons. Three of the buildings had mechanical ventilation, while one was naturally ventilated. The suckler building had higher relative humidity (RH > 90 %) and NH<sub>3</sub> concentrations (> 25 ppm) due to lower minimum air change rate (ACH = 1.2 h<sup>-1</sup>). The suckler building also had the highest NH<sub>3</sub> emissions (2.04 g Livestock Unit (LU)<sup>-1</sup> h<sup>-1</sup>) followed by the mechanically ventilated dairy building (1.92 g LU<sup>-1</sup> h<sup>-1</sup>) with the highest ACH. These two buildings had the lowest stocking densities and floor areas. In contrast, the suckler building had the lowest CH<sub>4</sub> emissions (6.8-10.7 g LU<sup>-1</sup> h<sup>-1</sup>). Methane emissions from the dairy building with the supply-exhaust air mixing system (16.4-19.3 g LU<sup>-1</sup> h<sup>-1</sup>) was higher than the other dairy buildings (11.7-13.8 g LU<sup>-1</sup> h<sup>-1</sup>). Temperature influenced NH<sub>3</sub> emissions however, the direction of association between temperature and NH<sub>3</sub> emissions differed among buildings. Relationship between RH and NH<sub>3</sub> emissions was positive, but the correlation coefficient (R<sup>2</sup> = 0.67) was strongest in the building with the highest RH.
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