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Energy and Carbon Costs of Selected Cow-Calf Systems
Authors:Cody J. Zilverberg  Phillip Johnson  Justin Weinheimer  Vivien G. Allen
Affiliation:1. Graduate Research Assistant, Department of Plant and Soil Science, Texas Tech University, Lubbock, TX 79409, USA;2. Professor, Texas Tech University, Lubbock, TX 79409, USA;3. Post-doc Research Associate, Department of Agricultural and Applied Economics, Texas Tech University, Lubbock, TX 79409, USA;4. Horn Professor, Department of Plant and Soil Science, Texas Tech University, Lubbock, TX 79409, USA;1. Department of Animal and Poultry Science, University of Saskatchewan, Saskatoon, SK, S7N 5A8, Canada;2. Western Beef Development Centre, Humboldt, SK, S0K 2A0, Canada;3. Department of Large Animal Clinical Sciences, University of Saskatchewan, Saskatoon, SK, S7N 5B4, Canada;4. Agriculture and Agri-Food Canada, Lacombe Research and Development Centre, 6000 C & E Trail, Lacombe, AB, T4L 1W1, Canada;5. Department of Agricultural, Food and Nutritional Science, University of Alberta, Edmonton, AB, T6G 2P5, Canada;2. Grazinglands Research Laboratory, USDA-ARS, El Reno, OK 73036;3. Department of Agricultural Economics and Agribusiness, Louisiana State University Agricultural Center, Baton Rouge 70803;4. Department of Experimental Statistics, Louisiana State University Agricultural Center, Baton Rouge 70803;1. Department of Meat Technology and Chemistry, Faculty of Food Sciences, University of Warmia and Mazury in Olsztyn, Plac Cieszyński 1, 10-719, Olsztyn, Poland;2. Department of Cattle Breeding and Milk Evaluation, Faculty of Animal Bioengineering, University of Warmia and Mazury in Olsztyn, Oczapowskiego 5, 10-719, Olsztyn, Poland
Abstract:Fossil fuel-derived inputs can increase cow-calf production per unit of land or labor but can raise financial and environmental concerns. Eleven US cow-calf systems from nine ecological regions in Iowa, South Dakota, Tennessee, and Texas were analyzed to determine quantities of energy used and carbon (C) emitted due to fossil fuel use (excluding emissions from soils and biota) and to determine how management and environment influenced those quantities. Total energy and C cost, calculated cow?1 or ha?1, were highly correlated (0.99). Energy use cow?1 and ha?1 varied greatly across systems, ranging from 3 000 to 12 600 megajoules (MJ) · cow?1 · yr?1 and from 260 to 20 800 MJ · ha?1 · yr?1. As stocking rate increased, MJ · cow?1 increased at an increasing rate. Differences in quantity of fertilizer accounted for most variation in energy use. Fertilizer allowed higher stocking rates but reduced energy efficiency of liveweight marketed. Compared to intensive, higher stocking rate systems, rangeland systems based on native or naturalized forages used little or no fertilizer, but used more energy cow?1 for crude protein (CP) supplementation, fencing, and pickup trucks. Across all systems, energy used to produce winter feed ranged from 0% to 46% of total energy. Northern systems used higher percentages of total energy for winter feed and fed for more days year?1, but southern systems that included large amounts of bermudagrass (Cynodon dactylon L.) hay used the most MJ · cow?1 for winter feed. Systems with high MJ · cow?1 were vulnerable to shocks in energy prices. Reducing energy use and C emissions from cow-calf operations is possible, especially by reducing fertilizer and hay use, but would likely reduce productivity ha?1. Forages with high nitrogen use efficiency, locally adapted plants and animals, and replacement of hay with unfertilized dormant forage and CP supplementation could reduce energy use.
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