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ARS Home Northeast Area University Park, Pennsylvania Pasture Systems & Watershed Management Research Docs





- Dairy Gas Emissions Model
- DairyGEM Download and Installation Instructions
- Beef Gas Emissions Model
- BeefGEM Download and installation Instructions
- Integrated Farm System Model
- IFSM Download and Installation Instructions
- Projected Future Climate Data for IFSM

Beef Gas Emissions Modelheadline bar /ARSUserFiles/80700500/images/BeefGEM.png Reference Manual for BeefGEM Download and installation instructions for BeefGEM  What is the Beef Gas Emissions Model? The Beef Gas Emissions Model (BeefGEM) is a software tool for estimating ammonia, hydrogen sulfide, volatile organic compound (VOC), and greenhouse gas (GHG) emissions of beef cattle production systems as influenced by climate and management. A production system generally represents the processes used on a given farm, ranch or feedlot, but the full system extends beyond the boundaries of the operation. A production system is defined to include emissions during the production of all feeds whether produced on the given farm or elsewhere. It also includes GHG emissions that occur during the production of resources used on the farm such as machinery, fuel, electricity, and fertilizer. Manure is assumed to be applied to cropland producing feed, but any portion of the manure produced can be exported to other uses external to the system. BeefGEM uses process level simulation to predict ammonia and hydrogen sulfide emissions from manure in the housing facility, during long term storage, following field application and during grazing. Process-based relationships and emission factors are used to predict the primary GHG emissions from the production system. Primary sources include the net emission of carbon dioxide plus all emissions of methane and nitrous oxide. All emissions are predicted through a daily simulation of feed use and manure handling. Daily emission values of each gas are summed to obtain annual values. Ammonia emissions occur from the barn floor, during manure storage, following field application, and during grazing. Barn floor emissions are determined separately for cow and replacement heifer facilities. For each facility, hourly emission rates are a function of the type of housing facility, the nitrogen level in excreted manure, temperature, air velocity, and other factors. When long term manure storage is used, ammonia emissions continue from the storage facility as a function of manure nitrogen and solids content, storage design, temperature, and wind velocity. Following field application of manure, ammonia is rapidly emitted unless it is incorporated by a tillage operation or directly injected into the soil. For grazing animals, ammonia is emitted from urine patches where the emission rate is again a function of temperature and wind velocity. Hydrogen sulfide emissions are predicted using a process-based model similar to that used for ammonia. Since hydrogen sulfide is created under anaerobic conditions, most of this emission occurs during anaerobic storage of manure. The barn floor or feedlot may also be an emitter with minor emissions following field application and during grazing. Emissions from the barn floor are related to the sulfide content of the manure, manure pH, air temperature, and air velocity. These same factors influence emissions during long-term storage where the anaerobic conditions are conducive to sulfide production. When stored manure is broadcast on fields, any sulfide remaining in the manure is quickly lost and further formation ceases under these aerobic conditions. Very small amounts of hydrogen sulfide are produced and released from feces deposits on pasture as influenced by temperature. VOC emission rates are controlled by the concentration of VOCs in silage or manure and their volatility. To represent total VOC emission from silage, four groups of VOCs which have the most potential to contribute to poor air quality are considered (acids, alcohols, esters, and aldehydes). For each VOC group, a given concentration in silage after fermentation is assigned considering silage type. Emission losses are predicted as influenced by temperature and air movement, and the remaining VOC mass is tracked as silage moves through the three stages of storage removal, feed mixing, and feeding. VOC emission during storage removal and mixing reduces the concentration of VOCs present in the remaining stages. A similar approach is used to predict VOC emissions from manure as it moves through the stages of housing facility, storage, and field application. For manure, three groups of VOCs (acids, alcohols, and aromatics) are tracked to estimate the total emission of reactive VOCs. Carbon dioxide emissions include the net annual flux in feed production and daily values from animal respiration and microbial respiration in manure on the barn floor and during storage. The annual flux in feed production is that assimilated in the feed minus that in manure applied to cropland. Emission of carbon dioxide through animal respiration is a function of animal mass and daily feed intake, and that from the floor is a function of ambient or barn temperature and the floor surface area covered by manure. Emission from a manure storage is predicted as a function of the volume of manure in the storage using an emission factor. Finally, carbon dioxide emission from fuel combustion in farm engines is proportional to the amount of fuel used in the production and feeding of feeds and the handling of manure. Methane emissions include those from enteric fermentation, the barn floor, manure storage, and feces deposited in pasture. Emission from enteric fermentation is a function of the metabolizable energy intake and the diet starch and fiber contents for the animal groups making up the herd. Daily emissions from the manure storage are a function of the amount of manure in the storage and the volatile solids content and temperature of the manure. Emissions following field application of manure are related to the volatile fatty acid content of the manure and the amount of manure applied. Emissions during grazing are proportional to the amount of feces deposited on the pasture; that emitted in the barn is a function of the amount of manure deposited in the barn, barn temperature, and the floor area covered by the manure. Nitrous oxide emissions are that emitted from crop and pastureland during the production of feeds with minor emissions from the manure storage and barn floor. An emission factor approach is used to estimate annual emissions in feed production where the emission is 1% of the fertilizer and manure N applied to cropland and 2% of that applied to pastureland. Emission from the crust on a slurry manure storage is a function of the exposed surface area. Total greenhouse gas emission is determined as the sum of the net emissions of the three greenhouse gases where methane and nitrous oxide are converted to carbon dioxide equivalent units (CO2e). The carbon footprint of milk production is this net of all greenhouse gas emissions divided by the milk produced. The net emission is determined through a partial life cycle assessment (LCA) of the production system including both primary and secondary sources. Primary emissions are those emitted from the farm or production system during the production process. Secondary emissions are those that occur during the manufacture or production of resources used in the production system. These resources include machinery, fuel, electricity, fertilizer, pesticides, and plastic. Farm gate life cycle assessments are also used to estimate the fossil energy footprint for the simulated production system.  Reference Manual for BeefGEM A reference manual provides a detailed description of the model including the algorithms and major functions used to simulate the dairy production system, determine gaseous emissions, and calculate a carbon footprint. **To view, print or save a copy of the Reference Manual (*.pdf), select this line.** To view this copy of the reference manual, Adobe Acrobat Reader must be available on your computer. This manual is also available within the help system of the model after it has been installed on your computer.  Download and installation instructions for BeefGEM BeefGEM is available for download to your computer. We like to keep a record of those using the model, so please register your name and additional information before downloading the program. You may pass this program on to others for their use, but we ask that you let us know who is using the model. This model is updated periodically as corrections are made or new information is added. If you are a frequent user of the model, you may want to check back to this web page every year to see if a more recent version is available. The file BGEMinstall.msi can be downloaded to your computer. This file contains all the files needed to install and use BeefGEM. This includes weather data for all 50 states of the United States. **For instructions on downloading and installing BeefGEM, select this line.**


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