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  • 1
    Electronic Resource
    Electronic Resource
    Springer
    Nutrient cycling in agroecosystems 52 (1998), S. 195-212 
    ISSN: 1573-0867
    Keywords: aquatic emissions ; N2O ; nitrogen transport ; watersheds ; nitrous oxide
    Source: Springer Online Journal Archives 1860-2000
    Topics: Agriculture, Forestry, Horticulture, Fishery, Domestic Science, Nutrition
    Notes: Abstract The purpose of the current paper is to estimate future trends (up to the year 2050) in the global geographical distribution of nitrous oxide (N2O) emissions in rivers, estuaries, and continental shelf regions due to biological processes, particularly as they are affected by anthropogenic nitrogen (N) inputs, and to compare these to 1990 emissions. The methodology used is from Seitzinger and Kroeze (1998) who estimated 1990 emissions assuming that N2O production in these systems is related to nitrification and denitrification. Nitrification and denitrification in rivers and estuaries were related to external inputs of nitrogen to those systems. The model results indicate that between 1990 and 2050 the dissolved inorganic nitrogen (DIN) export by rivers more than doubles to 47.2 Tg N in 2050. This increase results from a growing world population, associated with increases in fertilizer use and atmospheric deposition of nitrogen oxides (NOy). By 2050, 90% of river DIN export can be considered anthropogenic. N2O emissions from rivers, estuaries and continental shelves are calculated to amount to 4.9 (1.3 – 13.0) Tg N in 2050, of which two-thirds are from rivers. Aquatic emissions of N2O are calculated to increase faster than DIN export rates: between 1990 and 2050, estuarine and river emissions increase by a factor of 3 and 4, respectively. Emissions from continental shelves, on the other hand, are calculated to increase by only 12.5%.
    Type of Medium: Electronic Resource
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  • 2
    Electronic Resource
    Electronic Resource
    Springer
    Mitigation and adaptation strategies for global change 1 (1996), S. 115-137 
    ISSN: 1573-1596
    Source: Springer Online Journal Archives 1860-2000
    Topics: Energy, Environment Protection, Nuclear Power Engineering , Geography
    Notes: Abstract The purpose of this study is to give a general overview of strategies to reduce N2O emissions and to investigate their potential effects in the Netherlands. For all major sources of N2O, technologies to reduce emissions are available or could become available in the near future. Their potential to reduce emissions has been estimated for conventional power plants (〉 10%), fluidized bed combustion (〉80%), industrial production of adipic acid (〉98%) and nitric acid (〉80%), municipal solid waste incineration (〉 10%) and sewage treatment plants (50%). In addition, it is estimated that fertilizer-induced emissions in intensive agriculture can be reduced by at least 65%. In the Netherlands, these strategies could reduce emissions of N2O by at least 40% in 1990 (i.e. if the technologies were fully implemented and nothing else would change) and by at least 30% in 2010 (relative to business as usual). Taking trends in activities into account, the mix of options considered could, in the period 2000–2010, reduce the annual Dutch emission to about 75% of the 1990 level. Most of this potential reduction is achieved by a catalytic reduction step in nitric acid production. Development of a catalytic converter seems feasible within a few years. The reduction options considered do not include additional reductions in the volumes of activities. Thus emissions could be further reduced by reductions in fossil fuel use, vehicle use, nitrogen fertilizer use, manure production, and waste production. Conceivable technologies that may not be implementable before 2000 include a number of promising options, such as low NO x engines in vehicles, electric vehicles, NO x reduction with low N2O formation in stationary combustion and the development of modified combustors.
    Type of Medium: Electronic Resource
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  • 3
    Electronic Resource
    Electronic Resource
    Springer
    Mitigation and adaptation strategies for global change 1 (1996), S. 115-137 
    ISSN: 1573-1596
    Source: Springer Online Journal Archives 1860-2000
    Topics: Energy, Environment Protection, Nuclear Power Engineering , Geography
    Notes: Abstract The purpose of this study is to give a general overview of strategies to reduce N2O emissions and to investigate their potential effects in the Netherlands. For all major sources of N2O, technologies to reduce emissions are available or could become available in the near future. Their potential to reduce emissions has been estimated for conventional power plants (〉10%), fluidized bed combustion (〉80%), industrial production of adipic acid (〉98%) and nitric acid (〉80%), municipal solid waste incineration (〉10%) and sewage treatment plants (50%). In addition, it is estimated that fertilizer-induced emissions in intensive agriculture can be reduced by at least 65%. In the Netherlands, these strategies could reduce emissions of N2O by at least 40% in 1990 (i.e. if the technologies were fully implemented and nothing else would change) and by at least 30% in 2010 (relative to business as usual). Taking trends in activities into account, the mix of options considered could, in the period 2000–2010, reduce the annual Dutch emission to about 75% of the 1990 level. Most of this potential reduction is achieved by a catalytic reduction step in nitric acid production. Development of a catalytic converter seems feasible within a few years. The reduction options considered do not include additional reductions in the volumes of activities. Thus emissions could be further reduced by reductions in fossil fuel use, vehicle use, nitrogen fertilizer use, manure production, and waste production. Conceivable technologies that may not be implementable before 2000 include a number of promising options, such as low NO x engines in vehicles, electric vehicles, NO x reduction with low N2O formation in stationary combustion and the development of modified combustors.
    Type of Medium: Electronic Resource
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  • 4
    ISSN: 1573-0867
    Keywords: animal waste ; fertilizer ; greenhouse gas ; inventory ; nitrous oxide
    Source: Springer Online Journal Archives 1860-2000
    Topics: Agriculture, Forestry, Horticulture, Fishery, Domestic Science, Nutrition
    Notes: Abstract In 1995 a working group was assembled at the request of OECD/IPCC/IEA to revise the methodology for N2O from agriculture for the National Greenhouse Gas Inventories Methodology. The basics of the methodology developed to calculate annual country level nitrous oxide (N2O) emissions from agricultural soils is presented herein. Three sources of N2O are distinguished in the new methodology: (i) direct emissions from agricultural soils, (ii) emissions from animal production, and (iii) N2O emissions indirectly induced by agricultural activities. The methodology is a simple approach which requires only input data that are available from FAO databases. The methodology attempts to relate N2O emissions to the agricultural nitrogen (N) cycle and to systems into which N is transported once it leaves agricultural systems. These estimates are made with the realization that increased utilization of crop nutrients, including N, will be required to meet rapidly growing needs for food and fiber production in our immediate future. Anthropogenic N input into agricultural systems include N from synthetic fertilizer, animal wastes, increased biological N-fixation, cultivation of mineral and organic soils through enhanced organic matter mineralization, and mineralization of crop residue returned to the field. Nitrous oxide may be emitted directly to the atmosphere in agricultural fields, animal confinements or pastoral systems or be transported from agricultural systems into ground and surface waters through surface runoff. Nitrate leaching and runoff and food consumption by humans and introduction into sewage systems transport the N ultimately into surface water (rivers and oceans) where additional N2O is produced. Ammonia and oxides of N (NOx) are also emitted from agricultural systems and may be transported off-site and serve to fertilize other systems which leads to enhanced production of N2O. Eventually, all N that moves through the soil system will be either terminally sequestered in buried sediments or denitrified in aquatic systems. We estimated global N2O–N emissions for the year 1989, using midpoint emission factors from our methodology and the FAO data for 1989. Direct emissions from agricultural soils totaled 2.1 Tg N, direct emissions from animal production totaled 2.1 Tg N and indirect emissions resulting from agricultural N input into the atmosphere and aquatic systems totaled 2.1 Tg N2O–N for an annual total of 6.3 Tg N2O–N. The N2O input to the atmosphere from agricultural production as a whole has apparently been previously underestimated. These new estimates suggest that the missing N2O sources discussed in earlier IPCC reports is likely a biogenic (agricultural) one.
    Type of Medium: Electronic Resource
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