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LCA Food 2012 in Saint Malo, France! - Manifestations et colloques ...

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PARALLEL SESSION 6C: POULTRY AND PORK PRODUCTION SYSTEMS 8 th Int. Conference on <strong>LCA</strong> <strong>in</strong> the<br />

Agri-<strong>Food</strong> Sector, 1-4 Oct <strong>2012</strong><br />

566<br />

Life cycle assessment of pig slurry treatment technologies<br />

M. ten Hoeve 1,* , S. Bruun 1 , L.S. Jensen 1 , N.J. Hutch<strong>in</strong>gs 2 , R. Jensen 2<br />

1 University of Copenhagen, Faculty of Life Sciences, Department of Agriculture and Ecology, Thorvaldsensvej 40, 1871 Frederiks-<br />

berg C, Denmark.<br />

2 Aarhus University, Department of Agroecology, Blichers Allé 20, 8830 Tjele, Denmark.<br />

Correspond<strong>in</strong>g author. E-mail: mtho@life.ku.dk<br />

ABSTRACT<br />

Animal manure management is associated with negative impacts on global warm<strong>in</strong>g, acidification and eutrophication of ecosystems.<br />

In the current study an <strong>LCA</strong> is used to assess the environmental impacts of treatment of 1000 kg of slurry ex-animal of five different<br />

technologies. These technologies are (a) direct land application (reference scenario), (b) separation by mechanical screw press, (c)<br />

screw press separation and compost<strong>in</strong>g of the solid fraction, (d) separation by decanter centrifuge, and (e) decanter centrifuge separation<br />

with ammonia stripp<strong>in</strong>g of the liquid fraction. In all separation scenarios, the liquid fraction was land applied close to the farm<br />

and the solid fraction was transported and land applied 100 km from the farm. In general, the treatment technologies analysed <strong>in</strong> this<br />

<strong>LCA</strong> show environmental impact potential reduction compared with the reference scenario. The decanter centrifuge scenarios have<br />

equal or lower impact potentials than the screw press scenarios. Relative rank<strong>in</strong>g of scenarios does not change after the sensitivity<br />

analysis, where field emission factors for N2O, NH3 and P were varied with<strong>in</strong> the range observed <strong>in</strong> literature. Choice of the technology<br />

to implement <strong>in</strong> any given situation depends on the environmental problem <strong>in</strong> focus.<br />

Keywords: life cycle assessment, pig slurry, slurry treatment technologies<br />

1. Introduction<br />

Large amounts of animal manure are produced <strong>in</strong> Europe and its management is associated with a number<br />

of environmental impacts. Impact categories that are ma<strong>in</strong>ly affected by animal manure management are (a)<br />

global warm<strong>in</strong>g potential, caused by m<strong>et</strong>hane and nitrous oxide emissions, (b) acidification potential, <strong>in</strong>duced<br />

by ammonia emissions, and (c) eutrophication potential caused by nitrogen and phosphorus emissions.<br />

These impacts are accentuated because an <strong>in</strong>creas<strong>in</strong>g share of agricultural land <strong>in</strong> Europe receives excessive<br />

amounts of animal manure. These so-called hotspot areas are characterised by high livestock densities<br />

and <strong>in</strong>sufficient land for manure application. This has resulted <strong>in</strong> phosphorus surplus <strong>in</strong> these areas and associated<br />

risks for losses to the environment. In other areas, agricultural fields do not receive sufficient amounts<br />

of nutrients from manure and farmers need to apply m<strong>in</strong>eral fertilisers to their fields. Non-renewable natural<br />

resources like phosphate rock, oil and natural gas, are used for the production of m<strong>in</strong>eral fertiliser and there<br />

are considerable environmental emissions, such as CO2 and phosphate leach<strong>in</strong>g, related to the extraction,<br />

manufactur<strong>in</strong>g and use of these fertilisers. In order to decrease the consumption of m<strong>in</strong>eral fertiliser and<br />

avoid losses from areas with excessive availability of animal manure, geographical redistribution of animal<br />

manure needs to improve.<br />

To enhance nutrient re-distribution, slurry treatment technologies have been developed that focus on the<br />

separation of slurry <strong>in</strong>to a solid and a liquid fraction. The liquid fraction conta<strong>in</strong>s most of the easily available<br />

nitrogen but less than half of the phosphorus, so is ma<strong>in</strong>ly valued as a nitrogen fertiliser. However, the high<br />

water content <strong>in</strong> the liquid fraction makes the fraction relatively heavy and less suitable for long distance<br />

transportation. Agricultural land nearby the farm often has been treated with slurry for multiple years, which<br />

implies that phosphorus concentrations <strong>in</strong> the soil are already sufficiently high to supply the crop demand.<br />

The solid fraction is more transportable, due to its relatively low water content. It has a high concentration of<br />

slowly-available nitrogen and phosphorus, so is ma<strong>in</strong>ly valuable as a phosphorus fertiliser. Additional technologies<br />

that are developed to avoid environmental impacts <strong>in</strong>clude ammonia stripp<strong>in</strong>g from the liquid fraction,<br />

which reduces emissions of ammonia, various technologies for energy extraction and upgrad<strong>in</strong>g of the<br />

solid fraction such as compost<strong>in</strong>g which may improve the solid fraction as a soil amendment.<br />

The objectives of this study are to d<strong>et</strong>erm<strong>in</strong>e environmental impact potentials of slurry treatment technologies<br />

<strong>in</strong> a Life Cycle Assessment (<strong>LCA</strong>) and to compare impact potentials of treatment technologies with<br />

a reference.<br />

2. M<strong>et</strong>hods<br />

2.1. Model description<br />

The <strong>LCA</strong> is based on <strong>in</strong>formation from literature research. The <strong>LCA</strong> itself was conducted by us<strong>in</strong>g the<br />

GaBi software (www.pe-<strong>in</strong>ternational.com). The functional unit that forms the basis for the assessment is the<br />

handl<strong>in</strong>g of 1000 kg of slurry excr<strong>et</strong>ed by pigs. Emissions from slurry, liquid and solid fractions were ana-

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