Does nitrogen cycle ? : changes in the spatial dynamics of nitrogen with industrial nitrogen fixation

Industrialization of the N cycle after World War II made new spatial dimensions in the movement of N in agriculture and society possible. Nitrogen fertilizer consumption in the USA increased from less than 0.5 million tons/yr in 1940 to more than 11 million tons/yr in 1980. Not only were crop and animal productivity increased with the increased availability, but specialized crop production and animal production regions developed. With N fertilizer available, N in feeds imported to animal production regions does not have to be returned to sustain crop production. Therefore, understanding the biology of N in the farm-level N cycle in either type of production region will be insufficient to understand the consequences of the one-way transfers of N between production regions. An environmental issue associated with the industrialization of N fixation is the depletion of nonrenewable fossil energy reserves to produce and transport fertilizers and agricultural products. Another is the reduced efficiency of N use in crop production as a result of increasing N inputs and the extent of the areas planted to N-fertilized crops. Nitrogen accumulation in manure in animal production regions poses another threat to the environment. Resolving contentious environmental issues may depend on research and management approaches that are consistent with the new spatial dimensions of N movement and the interests of all stakeholders

[1]  Gregory M. Perry,et al.  The On-Farm Costs of Reducing Groundwater Pollution , 1991 .

[2]  Prof. Dr. Carl Olof Tamm Nitrogen in Terrestrial Ecosystems , 1991, Ecological Studies.

[3]  N. L. Hargett,et al.  1986 Fertilizer Summary Data , 1985 .

[4]  Rodney L. Clouser,et al.  The Economic Impact of Regulatory Decisions in the Dairy Industry: A Case Study In Okeechobee County, Florida, , 1994 .

[5]  H. Pionke,et al.  Effect of Agricultural Land Use on Ground-Water Quality in a Small Pennsylvania Watersheda , 1985 .

[6]  S. B. Nott,et al.  Trends in the Management of Dairy Farms Since 1956 , 1981 .

[7]  B. R. Bock,et al.  Fertilizer Nitrogen Management , 1991 .

[8]  W. McSweeney,et al.  An Information Management Technology Program for ex ante Nutrient Loss Reduction from Farms , 1992 .

[9]  Michael P. Russelle,et al.  Nitrogen Cycling in Pasture and Range , 1992 .

[10]  K. D. Frank,et al.  Maize Production Impacts on Groundwater Quality , 1991 .

[11]  S. Bacon,et al.  Plant nutrient flow in the managed pathways of an intensive dairy farm. , 1990 .

[12]  Delwiche Cc The Nitrogen Cycle , 1970, Soil Microbiology.

[13]  W. Ritter Water quality of agricultural coastal plain watersheds , 1986 .

[14]  D. Jenkinson,et al.  An introduction to the global nitrogen cycle. , 1990 .

[15]  H. V. D. Meer,et al.  The relationship between inputs and outputs of nitrogen in intensive grassland systems , 1986 .

[16]  L. E. Asmussen,et al.  Relationship of Geology, Physiography, Agricultural Land Use, and Ground‐Water Quality in Southwest Georgiaa , 1985 .

[18]  R. H. Fox,et al.  Soil nitrate accumulations following nitrogen-fertilized corn in Pennsylvania , 1990 .

[19]  S. Batie Agriculture as the Problem: New Agendas and New Opportunities , 1988, Journal of Agricultural and Applied Economics.

[20]  L. Lanyon,et al.  Plant nutrient management strategy implications for optimal herd size and performance of a simulated dairy farm , 1989 .