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 tonslyr 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 oneway 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. Research Question Fertilizer N and animal manure are often implicated in the claims of environmental pollution from agriculture. This study attempts to evaluate the changes in agriculture and society that have taken place since fertilizer N became widely available. Understanding these changes may provide the basis for a comprehensive approach to reducing N losses from agriculture. Literature Summary The history of fertilizer use in the USA clearly documents the dramatic increase in fertilizer N use since the mid-1940s. Historic approaches to dealing with the movement of N in the environment and agriculture generally focus on N “cycling.” Recent developments in ecological theories suggest that observations of the world at different scales can provide new ways to organize information and stimulate new insights into every day activities. Study Description Agricultural statistics about fertilize N use, crop and animal productivity, and the locations of crop and animal production were evaluated to determine if N cycles within the existing managed pathways of agriculture and society. Applied Questions Does N cycle? Fertilizer N use in the USA increased from less than 0.5 million tons/yr to over 11 million in less than 50 yr. Also, the concentration of fertilizer N use moved from the southeastern USA to the north central USA. This change in fertilizer N use, especially for corn production, was accompanied by an increase in soybean production for the oilseed. Consequently, the basis for the concentration of animal production on few large farms outside the feed grain production areas was established. Even ruminant animal rations, such as for dairy cows, now emphasize concentrates, including corn and soybean oil meal. The spatial pattern of change in the relative importance of livestock and crop cash farm receipts to regional US agriculture was opposite to the new patterns in fertilizer N use. The difference between these two patterns reflects the ability to produce livestock and poultry outside the regions of intensive crop production. With the development of animal production regions, N no longer cycles within individual farm boundaries. Nitrogen in agriculture must be managed for efficient throughput in the crop production areas and for effective distribution as it accumulates in animal production regions. Will N cycling information help improve N management? Nitrogen management is no longer related only to the land base of an individual farm, but rather to the use of fertilizer N and animal feed as capital factors of production. Additional detailed farm-level N cycling information may provide limited improvements in N management to avoid unacceptable losses from agriculture. As an alternative, ways of measuring N movement in agriculture at regional and interregional scales must be researched. These new measurements and the resulting insights will complement new decisionmaking procedures that involve all the stakeholders in N management including farmers, community and business leaders, and the special interests of consumers and environmentalists. Current approaches to voluntary or regulatory change focus on farmer management of N recovery efficiency in crop production or different management of land-applied manure. With the separation of crop production and animal production, neither of these are adequate nor do they include all the stakeholders. Recommendation More emphasis should be placed on researching and monitoring the movement of N beyond the boundaries of individual farms and on developing comprehensive management approaches based on spatially extended N pathways, not just farm-level cycling. Better data for regional N budgets, new theories to organize large scale information, and new management procedures with multi-organizational participation to protect common water resources from N pollution should be developed.
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