Titlebook: Gaseous Loss of Nitrogen from Plant-Soil Systems; J. R. Freney,J. R. Simpson Book 1983 Springer Science+Business Media Dordrecht 1983 evol

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n gaseous forms as ammonia, nitrous oxide, nitric oxide or dinitrogen. The leached nitrate can contaminate rivers and ground waters, while the emitted ammonia can contaminate surface waters or combine with atmospheric sulfur dioxide to form aerosols which affect visibility, health and climate. There is also c978-90-481-8276-3978-94-017-1662-8

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Gaseous nitrogen losses from plants,his physiological period proteins break down in senescing leaves, liberating NH. (Thimann 1980). Gaseous losses of NH. are therefore possible, and have indeed been found. Gaseous losses of other reduced forms and of oxidized forms have also been found. In addition, losses as N. have been postulated.

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Agronomic and technological approaches to minimizing gaseous nitrogen losses from croplands,hemical properties of N fertilizers, and improved crop and soil management practices. Some of the methods directed toward reducing gaseous N loss from cultivated soils also may increase the efficiency of plant use of N by decreasing the movement of inorganic N in solution from the plant rhizosphere,

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978-90-481-8276-3Springer Science+Business Media Dordrecht 1983

Evolve

Information, Welfare, and Product Diversitys presence is readily detectable near barns, stables and feedlots where plant and animal residues are concentrated but it is also formed in many other situations from less concentrated sources, e.g. in fields and forests (Lemon and Van Houtte 1980). It is constantly being formed in soils at rates wh

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https://doi.org/10.1007/978-3-662-11174-1the soil. It was generally assumed that the important pathways of loss were volatilization of NH., and reduction of nitrate to N.O and N. by soil microorganisms (biological denitrification). There was little direct evidence to support the assumption of significant losses via these pathways, despite