A method for livestock waste management planning in NE Spain
Section snippets
Minimization
Minimization of the generation of residues is crucial and one of the cheapest strategies to be adopted, becoming a must, previous to any other action.
Use of livestock wastes as fertilizers and nitrogen balance
The use of livestock wastes instead of mineral fertilizer has the following main limitations (Tabaglio et al., 1992):
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relatively low nutrient concentrations. Therefore fertilization with livestock wastes is expensive due to the need to transport large amounts of waste,
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difficulty in determining the nutrient concentrations in the wastes. The absence or low efficiency of homogenizers in the waste stocking tanks makes it difficult to determine the real nutrient content of wastes. This can be solved
Spatial distribution of nutrient generation
Regional or municipal balances may provide a distorted image of the problems since the actual spatial distribution of the crop requirements is often not known. The balance result will also depend on the scale of the analysis. In this sense, it is interesting noticing that, in Spain, the yearly nitrogen generation in the wastes from intensive farming corresponds to an average charge of 21 kg N/ha year. These values coincide with values from the US Southwest, where 50 1b/Ac are common (Cadena,
Transportation costs
Waste transportation constitutes the real bottleneck of the management of surplus livestock waste. Transportation cost varies per unit volume transported with the distance, and its incidence changes remarkably if the nutrients contained in the waste are given a value (Sangiorgi and Balsari, 1992). This is especially true where there's still land available for animal wastes application as fertilizer nearby the livestock farms.
Transportation is limiting because the wastes are highly diluted, the
Deciding on the treatment objectives
As Hahne et al. (1996) stated, the environmental effect of livestock farming depends on the number of animals and their concentration relative to the available area for livestock waste utilization in accordance with a good agricultural practice. For farms without a livestock waste surplus, its utilization probably will probably not cause any environmental pollution if the waste is stored in covered tanks for long enough and applied with flushing or injection systems or worked into the soil
Economic scoring of centralized surplus waste treatment plants
As already mentioned, in localized surplus nitrogen areas, the alternatives are either moving the farms out of the area, or reducing the waste volume to decrease export costs. In Spain, this second option is being favored through the Spanish Royal Decree 2818/1998 of 23 December on energy, cogeneration and wastes (and its yearly updates). This decree establishes a subsidy for the electricity produced by cogeneration if waste thermal energy is used for reducing the volume of pig slurry, sewage
Conclusions
The development of livestock wastes management planning, decision and control tools is necessary. Global long term planning is needed for the management of livestock residue in order to guarantee farm survival and the preservation of the environment.
Minimization of the generated wastes is a powerful tool that needs further development, research, and implementation efforts.
A management plan must be based on the nutrients balance according to local crop needs, on guarantying enough storage
Acknowledgements
We wish to thank all the municipalities, farmer associations, individuals and students who helped identifying the UTM co-ordinates of the farms, J. Areny for his collaboration, and the Catalan Ministries of Agriculture, Livestock and Fisheries and that of Environment for funding (University of Lleida, CTT project K0011) and facilitating data on livestock numbers and crops.
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