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Energy consumption in the cycle of fertilizers

It is very difficult to measure how much a chemical fertilizer emits GHG to the atmosphere once we use it in the field. But when we look at the life cycle of the production and use of fertilizer we can take a decision as to which fertilizer is eco-friendly and emits less GHG in the atmosphere.
 
The life cycle of fertilizer contributes significantly to the overall impact of conventional agriculture. The production of fertilizers is energy intensive, and emits about 1.2% of the world's total GHGs (Wood and Cowie, 2004). Generally, fertilizers containing N compounds consume up to 10 times more energy and consequently result in more GHG emissions. In comparison, fresh manure is a very low carbon emitting alternative when it is available to provide land with nutrients (Lal, 2004c). However, the actual energy consumed during the production can vary widely as very modern plants have the potential to efficiently use the heat produced during the reaction process and hence may even have a negative energy balance, for production of nitrate will also generate nitrous oxide as a by-product. Considering that nitrous oxide has a global warming potential of ~296 compared to carbon dioxide, this is the main GHG in the nitrate production (Brentrup et al., 2004) (Wood and Cowie, 2004). As a result, nitrous oxide contributes 26% of the global total fertilizer production GHG emissions (Kongshaug, 1998).

Additional greenhouse gas emissions will arise from the transport of these fertilizers as mines are not evenly distributed around the world (www.fertilizer.org). Generally, transport and storage will add more to the total GHG emission of fertilizer use. 
 
The final use of the fertilizer on the farm will have again a variety of impacts. The machinery used to apply the fertilizer will require fuel, adding to the GHG emissions. Fertilizers are not used fully by the crop, which on average globally only recover about 50% of fertilizer N supplied (Eickhout et al., 2006).
 
Consequently, a great proportion accumulates in soils and is either lost directly as nitrous oxide, or leaches into water courses, enhancing downstream, indirect nitrous oxide emissions. The amount lost will greatly depend on many other factors such as climate, soil and management practices (Brentrup et al., 2004) (Eickhout et al., 2006).


Cool farming report, Greenpeace, January 2008 [R.E31d.40]
 

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