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Methane Emissions From Domestic Animals

Methane produced during digestion is a significant part of the global methane budget.  As food is digested, microbes break down the organic matter creating methane by enteric fermentation.  Ruminant animals, such as cows, emit an especially large amount of methane through their digestive process.  In Rhode Island, the most significant methane from animal sources originates from livestock on farms.  The calculated emissions from this source were 3,566 MTCE in 1990, and 3,465 MTCE in 1996.  These emissions account for only approximately 0.03% of the total greenhouse gas emissions in Rhode Island. 

             The methodology used comes from the Workbook. The data that are needed to estimate these emissions are the populations of domestic animals.  The population data are multiplied by an emission factor that is provided by the workbook for each type of animal.  The data used for these calculations are shown in the Appendix -  Agriculture - Table 1-1.

             There was an overall decrease in the amount of emissions that resulted from the digestive process of domesticated animals from 1990 to 1996, as shown in the Domesticated Animal Figure  This was caused by an overall decrease in the number of domestic animals in the State over this time.

             The animal population data came from the 1996 National Agricultural Statistics Service. Data were not available for all animals, for every year.  Some of the values used where interpolated between years that were accounted for.  This adds to the uncertainty of the calculations.  The census of animals occurred on January 1st of each of the census years.  Fluctuations in animal populations throughout the year are not taken into account in the numbers used, which has some influence on the emissions.  Also, other factors not directly taken into account in the calculations include: the feeding situation of the animals, work performed by the animals, and the feed digestibility.  There was insufficient data to incorporate these factors into the calculations, so the average values provide in the Workbook were used. 

                         
 

 

Methane Emissions From Manure Management

                 Methane is produced by the anaerobic decomposition of the organic matter in manure.  The amount of methane produced by manure varies depending on the storage system used to manage it. Methane emissions from manure management appears to make an insignificant contribution to the total greenhouse gas emissions in Rhode Island, amounting to only 0.005% of all emissions in 1996.  The total emissions from manure in 1990 were 762 MTCE, in 1996 they where 635 MTCE. 

                The methodology used comes from the Workbook: Chapter 7.  The emissions are estimated as a function of the domestic animal population, and the types of waste management systems used.  The calculations and data that were used to estimate the emissions are located in the Appendix - Agriculture Tables 2-1 through 2-13.

                 There was an overall decrease in the amount of methane emitted from manure management from 1900 to 1996, as shown in the graph below. This decrease is due largely to a decrease in the amount of mature dairy cattle in Rhode Island over the inventory years.  The emissions estimated for each animal group are shown in the Appendix -Agriculture: Table 2-14. 

                The same population values were used in this section as in the section for methane emissions from Domestic Animals.  The same difference between the animal populations that were used in these calculations from the average applies in this section.  Another source of uncertainty was the different manure management systems used in the state.  Statewide averages were used to estimate the amount of manure that went into different systems. Since, state data were not available for the management systems used for sheep manure, the national averages were used. 

 

 

  

Emissions from Agricultural Soils

                 Agriculture soil management practices are a net source of nitrous oxide. Other agricultural sources of nitrous oxide emissions include, manure management practices, and lime applied to soils.  The total nitrous oxide emissions from soils were 2,796 MTCE in 1990 and 2,189 MTCE in 1996.  Emissions from agricultural soils represent approximately 0.03% of all of Rhode Islands greenhouse gas emissions. 

                 The methodology used to estimate the emissions from agricultural soils comes from the Workbook, Chapter 9.  The emissions from synthetic fertilizers was estimated by multiplying the total amount of fertilizer nitrogen used by an emissions factor.  This emissions factor is the amount of N2O, in kilograms, emitted in each year, per kilogram of nitrogen applied to the soil in that year.  The N2O emissions from manure was estimated as a function of domestic animal population in the state in the inventory years. Details of these calculations are located in Appendix - Agriculture, Table 3-2.

                The change in emissions from nitrous oxide was mainly due to a decrease in the amount of synthetic fertilizer used in the state.   The changes in emissions from other sources where extremely small. The total emissions for each source of N2O is located in the Agriculture appendix.

                Data were unavailable for to estimate many potential sources of nitrous oxide Agriculture appendix.  This lack of data means there could be a substantial percentage error in the estimates of nitrous oxide emissions.  Also, the estimates of emissions from fertilizers are uncertain.  There are many factors that affect N2O emissions from fertilizer use, including soil pH and temperature, for which data are not available.  The Workbook multiplier that combines many variables into one factor, was used here.  Of course, since emissions of N2O make up an extremely small portion of the total greenhouse gas emissions in Rhode Island, this data gap introduces very little uncertainty into the overall inventory estimates. 

 

 

 

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Greenhouse Gas Inventory for Rhode Island  September 2000 

Prepared by Brown University Center For Environmental Studies