Nutrients/Description: Difference between revisions

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{{FormulaAndTableTemplate|Formula1_N}}
{{FormulaAndTableTemplate|Formula1_N}}


where  is human N emissions (kg per person per year), D is the fraction of the total population that is connected to public sewerage systems (no dimension), and R N is the overall removal of N through wastewater treatment (no dimension). Total P emissions to surface water are calculated in a similar way, but also include estimates of P emissions to surface water resulting from the use of P-based dishwasher and laundry detergents. Nutrient removal by wastewater treatment R is based on the relative contribution of four classes of treatment (none, primary, secondary and tertiary treatment). D (calculated from the fraction of households with improved sanitation) and R (by treatment class) are scenario variables.
where   
*is human N emissions (kg per person per year),  
*D is the fraction of the total population that is connected to public sewerage systems (no dimension),  
*R N is the overall removal of N through wastewater treatment (no dimension).  
Total P emissions to surface water are calculated in a similar way, but also include estimates of P emissions to surface water resulting from the use of P-based dishwasher and laundry detergents. Nutrient removal by wastewater treatment R is based on the relative contribution of four classes of treatment (none, primary, secondary and tertiary treatment). D (calculated from the fraction of households with improved sanitation) and R (by treatment class) are scenario variables.
==B. Soil nutrient budget model==
==B. Soil nutrient budget model==
The soil budget approach ([[Bouwman et al., 2009]]; [[Bouwman et al., 2011]]) includes the N and P input and output for IMAGE grid cells. Soil N budgets are calculated for two production systems (see figure on the right, B.), i.e. mixed and pastoral livestock production systems ([[Livestock]]). N input includes application of synthetic N fertiliser ([[HasAcronym::Nfert]]) and animal manure ([[HasAcronym::Nman]]), biological N fixation ([[HasAcronym::Nfix]]), atmospheric N deposition ([[HasAcronym::Ndep]]). Output includes N withdrawal from the field through crop harvesting, hay and grass cutting, and grass consumed by grazing animals ([[HasAcronym::Nwithdr]]). The soil N budget ([[HasAcronym::Nbudget]]) is calculated as follows:
The soil budget approach ([[Bouwman et al., 2009]]; [[Bouwman et al., 2011]]) includes the N and P input and output for IMAGE grid cells. Soil N budgets are calculated for two production systems (see figure on the right, B.), i.e. mixed and pastoral livestock production systems ([[Livestock]]). N input includes application of synthetic N fertiliser (Nfert) and animal manure (Nman), biological N fixation (Nfix), atmospheric N deposition (Ndep). Output includes N withdrawal from the field through crop harvesting, hay and grass cutting, and grass consumed by grazing animals (Nwithdr). The soil N budget (Nbudget) is calculated as follows:
{{FormulaAndTableTemplate|Formula2_N}}  
{{FormulaAndTableTemplate|Formula2_N}}  
For P the same approach is used, P input being animal manure and fertiliser. The soil nutrient budget ignores nutrient accumulation in soil organic matter in case of a positive budget (surplus), and soil organic matter decomposition and mineralisation. With no accumulation, a surplus represents a potential loss to the environment (for N this includes NH3 volatilisation ([[Emissions]]), denitrification, surface runoff and leaching; for P this is surface runoff).
For P the same approach is used, P input being animal manure and fertiliser. The soil nutrient budget ignores nutrient accumulation in soil organic matter in case of a positive budget (surplus), and soil organic matter decomposition and mineralisation. With no accumulation, a surplus represents a potential loss to the environment (for N this includes NH3 volatilisation ([[Emissions]]), denitrification, surface runoff and leaching; for P this is surface runoff).

Revision as of 15:23, 17 December 2013