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best available technologies for manure treatment - Baltic Green Belt

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Best Available Technologies <strong>for</strong> <strong>manure</strong> <strong>treatment</strong> baltic sea 2020<br />

1: INTRODUCTION AND BACKGROUND DESCRIPTION<br />

1: INTRODUCTION AND BACKGROUND DESCRIPTION<br />

1.1: Background<br />

Leaching of nutrients from sites with intensive<br />

rearing of livestock, also known as agricultural hot<br />

spots, has been identified by the Helsinki Commission<br />

as a prioritized area. Data shows that the amount<br />

of Phosphorous (P) and Nitrogen (N) in livestock<br />

<strong>manure</strong> spread on agricultural land by EU Member<br />

States in the <strong>Baltic</strong> Sea catchment area is 3–4 times<br />

higher than the amounts discharged from all households<br />

in the same area.<br />

Consultations have been done on the value and<br />

potential <strong>for</strong> <strong>Baltic</strong> Sea 2020 to address <strong>manure</strong><br />

handling at intensive livestock farming with e.g.<br />

HELCOM, Swedish Institute of Agricultural and Environmental<br />

Engineering (JTI), Swedish University<br />

of Agricultural Sciences (SLU), Swedish Environmental<br />

Research Institute (IVL) and the Federation <strong>for</strong><br />

Swedish Farmers (LRF). There is concordance on the<br />

importance to reduce nutrient leakage from intensive<br />

livestock farms to the <strong>Baltic</strong> Sea, through technical<br />

development and spreading of “Best Practices”.<br />

<strong>Baltic</strong> Sea 2020 has initiated a project to identify<br />

Best Available Technologies to reduce leaching of nutrients<br />

from farms with intensive rearing of pigs. The<br />

target area of the project is EU Member States of the<br />

<strong>Baltic</strong> Sea area: Sweden, Denmark, Poland, Germany,<br />

Finland, Estonia, Latvia, and Lithuania.<br />

Based on analyses of current projects and activities,<br />

existing EU legislation and with consideration<br />

to the sources of origin of N and P leaching to the<br />

<strong>Baltic</strong> Sea, the report focuses on:<br />

• Pig production in herds of more than 2.000 pigs<br />

• Technologies <strong>for</strong> <strong>manure</strong> <strong>treatment</strong> rather than<br />

practices <strong>for</strong> <strong>manure</strong> storage and spreading<br />

• Denmark and Poland’s parts of the <strong>Baltic</strong> Sea<br />

river basin area<br />

1.2: Turnover of N and P in the<br />

agricultural environment<br />

When focusing on the N and P in livestock <strong>manure</strong> it<br />

is important to clarify the process stage from animal<br />

to final disposal. Figure 1 indicates via indexes the typical<br />

retention of N and P in agricultural production<br />

systems that respect good agricultural practices – the<br />

rest is generally lost to the environment.<br />

N is lost to the environment both via emissions,<br />

leaching and run-off. Typically the emissions are<br />

relatively high in pig stables, but emissions can also<br />

happen from <strong>manure</strong> storages and in connection<br />

with spreading. Run-off happens if <strong>manure</strong> is spilled<br />

on the ground, if the floors in stables and the walls<br />

and floors of the <strong>manure</strong>s stores are not water tight,<br />

if there is a long time span between spreading of<br />

<strong>manure</strong> on the fields and the incorporation into the<br />

soil, or if livestock <strong>manure</strong> is spread on steep, frozen<br />

or water saturated soils.<br />

Nitrogen (N) leaching from livestock <strong>manure</strong>s happens<br />

especially as percolation through soil layers<br />

when it is applied on fields in an imprecise way, not<br />

being based on norms and fertiliser planning, or<br />

when it is distributed to bare soils or in any case at<br />

periods, ways and situations where the nutrients are<br />

Index of N amount: 100 80 75 50<br />

Phase:<br />

Manure leaving<br />

animal<br />

Manure leaving<br />

stable<br />

Manure leaving<br />

storage<br />

Re-circulated in the<br />

crop<br />

Index of P amount: 100 95 90 85<br />

Figure 1: Recirculation of N and P in the agricultural production, based on Poulsen & Kristensen (1998) and Birkmose<br />

et al. (2007) as concerns <strong>manure</strong> leaving animal, stable and storage, while indications <strong>for</strong> P as well as amounts<br />

re-circulated in the crop largely are own estimates in situations, where good agricultural practices are applied.<br />

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