Malé Declaration 1 ST emissions inventory workshop AIT, Bangkok, 3rd – 5th July 2006 Part 6 – Compilation of emissions from Agriculture (Sector 8) Harry.

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Presentation transcript:

Malé Declaration 1 ST emissions inventory workshop AIT, Bangkok, 3rd – 5th July 2006 Part 6 – Compilation of emissions from Agriculture (Sector 8) Harry Vallack, Stockholm Environment Institute (SEI) University of York, UK

Emissions from Agriculture Several types of agricultural practice emit pollutants relevant to the study of transboundary air pollution. Among these activities are: The first two are sources of ammonia (NH 3 ) emissions; the last one emits a range of air pollutants (NO x, SO x, CO, NMVOCs, NH 3, and particulate matter (PM)).  treatment of livestock manures  application of fertilizers  burning of agricultural residues

Emissions from Agriculture - Livestock Manure Management This covers emissions of ammonia (NH 3 ) from the storage and disposal of livestock manures for each of 10 categories of livestock. Emissions are calculated assuming an average nitrogen excretion rate for each category of animal and applying annually averaged emission factors (EFs) for:  Housing management (barns, stalls, stables), and  manure deposited during grazing. These EFs were derived for developing country regions

Emissions from Agriculture - Livestock Manure Management

Emissions from Agriculture - Emissions from Fertilizers  the type and amount of fertilizer applied  climate (i.e. mean spring air temperature)  the types of soils to which each fertilizer is applied (emissions are greater on calcareous soils) After application, some of the N contained in fertilizers is released to the atmosphere as ammonia (NH 3 ). These emissions depend on: A portion of fertilizer-N is also emitted as NO (assumed 0.7% by default)

Emissions from Agriculture - Emissions from Fertilizers Default emission factors in the EMEP/Corinair guidebook (detailed methodology) are presented for three climate categories:  Region A - mean spring air temperature > 13 ºC.  Region B - mean spring air temperature > 6 ºC but < 13 ºC, and  Region C - mean spring air temperature < 6 ºC There is also a ‘calcareous soil multiplier’ which should be entered if all the soils are calcareous (or modified according to the percentage calcareous soils using the equation provide at the bottom of the worksheet).

Emissions from Agriculture - Emissions from Fertilizers f Modify the multiplier (M new ) according to the percent calacarious soils (C) using using this equation: Mnew = ((C x M default ) + (100 - C))/100 Thus, for anhydrous ammonia, if only 25% of soils are calcarious, multiplier is reduced from 4 to 1.75.

Emissions from Agriculture - Emissions from Fertilizers Activity data – i.e. annual consumption of each type of fertilizer by country - are given in the FAOSTAT database for all years from Warning: data presented in the FAOSTAT database as ‘Mt’ are actually in ‘metric tonnes’ and not megatonnes (1,000,000 tonnes) as normally meant by ‘Mt’!

Emissions from Agriculture - burning of agricultural residues The steps include:  Finding activity data (e.g. from FAOSTAT) on the annual production of each crop (in kilotonnes)  For each crop, estimating the biomass of crop residue actually burned from: crop to residue ratios, dry matter fraction, fraction burned in fields, fraction oxidised,  Estimating CO emissions from the C fraction emitted as CO;  Estimating NO x emissions from the C:N ratio of the crop residues and an NO x emission ratio (fraction of total N released as NO x ); and  Estimating emissions of NMVOCs, NH 3 and PM by multiplying the amount of each crop residue burned by emission factors.

Emissions from Agriculture - emissions from burning of agricultural wastes

Compilation of emissions for Solvent and other product use (Sector 7) and for Agriculture (Sector 8) Practical session 7: 1.Filling in workbook with dummy data (see practical session 7 notes) 2.Plenary session – sharing problems encountered etc.