PBL Netherlands Environmental Assessment Agency

Surface N balance

Often farm-gate or whole system budgets, or balances, are created to study the environmental impact of N cycle acceleration in agricultural systems. These budgets [correct antecedent?] take into consideration the N input, and the output and total loss for the farm or system considered, without specifying where and in which form losses occur. Other studies use a lumped approach to estimate country surface N balance surpluses, without specifying the fate of the surplus N.

Geographically distributed N budgets for agro-ecosystems

PBL researchers focus on the geographic distribution of the balance and fate of nitrogen in the environment (Bouwman et al., 2005c). The surface N balance approach, which considers all relevant input, output and loss terms for a given land area, is therefore more appropriate than farm-gate or system balances. The budgets include both N inputs (N fertiliser, animal manure, biological N fixation and atmospheric N deposition) and outputs (including N removal from the field in harvested crops and grass, and grass consumption by grazing animals, along with ammonia volatilisation, denitrification and leaching). The surface N balance approach has now been incorporated into IMAGE 2.4 for calculating and presenting geographically distributed N budgets for agro-ecosystems (PBL ,then MNP, 2006).

Surface N balancing is based on the distribution of different crop and livestock production systems (mixed, landless and pastoral), as published in various PBL (then MNP) papers articles(Bouwman et al., 2005a; Bouwman et al., 2006b; Eickhout et al., 2006). Pastoral systems depend almost exclusively on grazing, while mixed and landless systems rely on a mix of concentrates (food crops) and roughage, consisting of grass, fodder crops, crop residues and other sources of feedstuffs. A model was developed to describe these two aggregated production systems for different world regions - each  system with typical production characteristics, for example, milk production per animal for dairy cattle, and off-take rates and carcass weights for non-dairy cattle, sheep and goats.

References

Bouwman AF ; Kram T ; Klein Goldewijk K (eds) (2006). Integrated modelling of global environmental change. An overview of IMAGE 2.4. Netherlands Environmental Assessment Agency

Bouwman L ; Hoek K van der ; Drecht G van ; Eickhout B (2006). World livestock and crop production systems, land use and environment between 1970 and 2030. In: Brouwer F, McCarl BA, eds. Agriculture and climate beyond 2015. A new perspective on future land use patterns. New York: Springer, 2006;75-89

Eickhout B ; Bouwman A F ; van Zeijts H (2006). The role of nitrogen in world food production and environmental sustainability. Agriculture, Ecosystems and Environment, 116: 4-14.

Bouwman AF ; Hoek KW van der ; Eickhout B ; Soenario I (2005). Exploring changes in world ruminant production systems. Agricultural Systems 2005; 84(2):121-53

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