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Variation in carbon footprint of milk due to management differences between Swedish dairy farms

Published online by Cambridge University Press:  31 March 2011

M. Henriksson*
Affiliation:
Department of Rural Buildings and Animal Husbandry, Swedish University of Agricultural Sciences, PO Box 86, SE-23053 Alnarp, Sweden
A. Flysjö
Affiliation:
Arla Foods amba, Sønderhøj 14, DK-8260 Viby J, Denmark Department of Agroecology and Environment, Aarhus University, PO Box 50, DK-8830 Tjele, Denmark
C. Cederberg
Affiliation:
SIK – the Swedish Institute for Food and Biotechnology, PO Box 5401, SE-40229 Gothenburg, Sweden
C. Swensson
Affiliation:
Department of Rural Buildings and Animal Husbandry, Swedish University of Agricultural Sciences, PO Box 86, SE-23053 Alnarp, Sweden Swedish Dairy Association, Scheelevägen 18, SE-223 63 Lund, Sweden
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Abstract

To identify mitigation options to reduce greenhouse gas (GHG) emissions from milk production (i.e. the carbon footprint (CF) of milk), this study examined the variation in GHG emissions among dairy farms using data from previous CF studies on Swedish milk. Variations between farms in these production data, which were found to have a strong influence on milk CF, were obtained from existing databases of 1051 dairy farms in Sweden in 2005. Monte Carlo (MC) analysis was used to analyse the impact of variations in seven important parameters on milk CF concerning milk yield (energy-corrected milk (ECM) produced and delivered), feed dry matter intake (DMI), enteric CH4 emissions, N content in feed DMI, N-fertiliser rate and diesel used on farm. The largest between-farm variations among the analysed production data were N-fertiliser rate (kg/ha) and diesel used (l/ha) on farm (CV = 31% to 38%). For the parameters concerning milk yield and feed DMI, the CV was approximately 11% and 8%, respectively. The smallest variation in production data was found for N content in feed DMI. According to the MC analysis, these variations in production data led to a variation in milk CF of between 0.94 and 1.33 kg CO2 equivalents (CO2e)/kg ECM, with an average value of 1.13 kg CO2e/kg ECM. We consider that this variation of ±17%, which was found to be based on the used farm data, would be even greater if all Swedish dairy farms were included, as the sample of farms in this study was not totally unbiased. The variation identified in milk CF indicates that a potential exists to reduce GHG emissions from milk production on both the national and farm levels through changes in management. As milk yield and feed DMI are two of the most influential parameters for milk CF, feed conversion efficiency (i.e. units ECM produced/unit DMI) can be used as a rough key performance indicator for predicting CF reductions. However, it must be borne in mind that feeds have different CF due to where and how they are produced.

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Full Paper
Copyright
Copyright © The Animal Consortium 2011

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References

Aronsson, H, Torstensson, G 2004. Beräkning av odlingsåtgärders inverkan på kväveutlakningen (Calculations of nitrate leaching due to different cropping methods). Ekohydrologi 78, Swedish University of Agricultural Sciences, division of water quality management, Uppsala.Google Scholar
Basset-Mens, C, Kelliher, FM, Ledgard, S, Cox, N 2009. Uncertainty of global warming potential for milk production on a New Zealand farm and implications for decision-making. The International Journal of Life Cycle Assessment 14, 630638.Google Scholar
Beever, DE, Doyle, PT 2007. Feed conversion efficiency as a key determinant of dairy herd performance: a review. Australian Journal of Experimental Agriculture 47, 645657.Google Scholar
Bertilsson, J 2001. Utvärdering av beräkningsmetodik för metanavgång från nötkreatur (Evaluation of calculation method for enteric fermentation of cattle). Internal report, Swedish Environmental Protection Agency, Stockholm, Sweden.Google Scholar
Britt, JS, Thomas, RC, Speer, NC, Hall, MB 2003. Efficiency of converting nutrient dry matter to milk in Holstein herds. Journal of Dairy Science 86, 37963801.Google Scholar
British Standard Institute 2008. PAS 2050:2008-Specification for the assessment of life cycle greenhouse gas emissions of goods and services. Department for Environment, Food and Rural Affairs, Carbon Trust, BSI, London, UK.Google Scholar
Cederberg, C, Flysjö, A 2004. Life cycle inventory of 23 dairy farms in South-Western Sweden. SIK report no. 728, Swedish Institute for Food and Biotechnology, SIK, Gothenburg, Sweden.Google Scholar
Cederberg, C, Flysjö, A, Ericson, L 2007. Livscykelanalys (LCA) av norrländsk mjölkproduktion (Lifecycle assessment of milk production in northern Sweden). SIK report no. 761, Swedish institute for food and biotechnology, SIK, Gothenburg, Sweden.Google Scholar
Cederberg, C, Sonesson, U, Henriksson, M, Sund, V, Davis, J 2009. Greenhouse gas emissions from Swedish production of meat, milk and eggs 1990 and 2005. SIK report no. 793, Swedish institute for food and biotechnology, SIK, Gothenburg, Sweden.Google Scholar
De Vries, M, de Boer, IJM 2009. Comparing environmental impacts for livestock products: a review of life cycle assessments. Livestock Science 128, 111.Google Scholar
Domburg, P, Edwards, AC, Sinclair, AH 2000. A comparison of N and P inputs to the soil from fertilizers and manures summarized at farm and catchment scale. Journal of Agricultural Science 134, 147158.CrossRefGoogle Scholar
Ellis, JL, Kebreab, E, Odongo, NE, McBride, BW, Okine, EK, France, J 2007. Prediction of Methane production from dairy and beef cattle. Journal of Dairy Science 90, 34563467.Google Scholar
Flysjö, A, Henriksson, M, Cederberg, C, Ledgard, SF, Englund, J-E 2011. Various parameters effect on the carbon footprint of milk production in New Zealand and Sweden. Agricultural Systems (submitted).CrossRefGoogle Scholar
Garnsworthy, PC 2004. The environmental impact of fertility in dairy cows: a modelling approach to predict methane and ammonia emissions. Animal Feed Science and Technology 112, 211223.CrossRefGoogle Scholar
Gerber, P, Vellinga, T, Opio, C, Henderson, B, Steinfeld, H 2010. Greenhouse gas emissions from the dairy sector – a life cycle assessment. Food and Agriculture Organisation of the United Nations, Animal Production and Health Division, Rome.Google Scholar
Gibbons, JM, Ramsden, SJ, Blake, A 2006. Modelling uncertainty in greenhouse gas emissions from UK agriculture at the farm level. Agriculture Ecosystems & Environment 112, 347355.CrossRefGoogle Scholar
Gill, M, Smith, P, Wilkinson, JM 2010. Mitigating climate change: the role of domestic livestock. Animal 4, 323333.CrossRefGoogle ScholarPubMed
Hospido, A, Sonesson, U 2005. The environmental impact of mastitis: a case study of dairy herds. Science of the Total Environment 343, 7182.Google Scholar
IPCC 2006a. N2O Emissions from managed soils, and CO2 emissions from lime and urea application. In IPCC Guidelines for National Greenhouse Gas Inventories – Volume 4 Agriculture, Forestry and Other land use. (ed. HS Eggleston, L Buendia, K Miwa, T Ngara and K Tanabe), National Greenhouse Gas Inventories Program IGES, Japan, 11.5–11.4.Google Scholar
IPCC 2006b. Emissions from livestock and manure management. In IPCC Guidelines for National Greenhouse Gas Inventories – Volume 4 Agriculture, Forestry and Other land use. (ed. HS Eggleston, L Buendia, K Miwa, T Ngara and K Tanabe), National Greenhouse Gas Inventories Program, IGES, Japan, 10.3510.70.Google Scholar
IPCC 2007. Climate change 2007: the physical science basis. Contribution of Working Group I to the 4th Assessment Report of the Intergovernmental Panel on Climate Change (ed. S Solomon, D Qin, M Manning, Z Chen, M Marquis, KB Averyt, M Tignor and HL Miller), Cambridge University Press, Cambridge, UK and New York, NY, USA, 1334.Google Scholar
International Organization for Standardization (ISO) 2006a. Environmental management – Life cycle assessment – Principles and framework. ISO 14040:2006(E). ISO, Geneva, Switzerland.Google Scholar
International Organization for Standardization (ISO) 2006b. Environmental management – Life cycle assessment – Requirements and guidelines. ISO 14044:2006(E). ISO, Geneva, Switzerland.Google Scholar
Jordbruksverket 2008. Växtnäringsbalanser och kväveutlakning på gårdar i Greppa Näringen åren 2000–2006 (Farm gate nutrient balances and nitrogen leaching on farms in the advisory program Focus on nutrient during the years 2000–2006). Report no. 25. Swedish Board of Agriculture, Jönköping.Google Scholar
Karlsson, S, Rodhe, L 2002. Översyn av Statistiska Centralbyråns beräkning av ammoniakavgången i jordbruket – emissionsfaktorer för ammoniak vid lagring och spridning av stallgödsel (Emission factors used for ammonia volatiled in the management of manure, used in calculations by the Statistics Sweden). Uppdragsrapport Swedish Institute of Agricultural and Environmental Engineering, Uppsala, Sweden.Google Scholar
Linder, J 2001. STANK – the official model for input/output accounting on farm level in Sweden. Element balances as a sustainable tool. Workshop in Uppsala, March 16 to 17, 2001. Report no. 281. JTI-Swedish Institute of Agricultural and Environmental Engineering, Uppsala, Sweden.Google Scholar
Lindgren, E 1980. Skattning av energiförluster i metan och urin hos idisslare. (Estimation of energy losses in methane and urine for ruminants). Report no. 47, Department of Animal Nutrition and Management, Swedish University of Agricultural Sciences, Uppsala, Sweden.Google Scholar
Lovett, DK, Shalloo, L, Dillon, P, O'Mara, FP 2008. Greenhouse gas emissions from pastoral based dairying systems: the effect of uncertainty and management change under two contrasting production systems. Livestock Science 116, 260274.Google Scholar
Place, SE, Mitloehner, FM 2010. Invited review: contemporary environmental issues: a review of the dairy industry's role in climate change and air quality and the potential of mitigation through improved production efficiency. Journal of Dairy Science 93, 34073416.CrossRefGoogle ScholarPubMed
PRé Consultants bv. 2010. SimaPro 7, LCA software. Amersfoort, The Netherlands. Retrieved February, 2011, from www.pre.nlGoogle Scholar
Rodhe, L, Ascue, J, Tersmeden, M, Ringmar, A, Nordberg, Å 2008. Greenhouse gases from cattle slurry storage. JTI-rapport 370 Swedish Institute of Agricultural and Environmental Engineering, Uppsala, Sweden.Google Scholar
Rypdal, K, Winiwarter, W 2001. Uncertainties in greenhouse gas emission inventories – evaluation, comparability and implications. Environmental Science & Policy 4, 107116.CrossRefGoogle Scholar
Soussana, JF, Tallec, T, Blanfort, V 2009. Mitigating the greenhouse gas balance of ruminant production systems through carbon sequestration in grasslands. Animal 4, 334350.Google Scholar
Stallings, CC, McGilliard, ML 1984. Lead factors for total mixed ration formulation. Journal of Dairy Science 67, 902907.CrossRefGoogle ScholarPubMed
Swensson, C 2002. Effect of manure handling system, N fertiliser use and area of sugar beet on N surpluses from dairy farms in southern Sweden. Journal of Agricultural Science 138, 403413.Google Scholar
Thomassen, MA, van Calker, KJ, Smits, MCJ, Iepema, GL, de Boer, IJM 2008. Life cycle assessment of conventional and organic milk production in the Netherlands. Agricultural Systems 96, 95107.Google Scholar
Winsten, JR, Kerchner, CD, Richardson, A, Lichau, A, Hyman, JM 2010. Trends in the Northeast dairy industry: large-scale modern confinement feeding and management-intensive grazing. Journal of Dairy Science 93, 17591769.CrossRefGoogle ScholarPubMed
Yan, T, Mayne, CS, Porter, MG 2006. Effects of dietary and animal factors on methane production in dairy cows offered grass silage-based diets. International Congress Series 1293, 123126.Google Scholar