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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 />

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

ANNEX E: TABLES WITH SHORT DESPRIPTION OF LIVESTOCK MANURE TREATMENT TECHNOLOGIES<br />

Ref No. 56 Aeration<br />

Brief description Description of the effect on leaching (positive or negative) of N and P<br />

The term “aerobic <strong>treatment</strong>” refers to biological <strong>treatment</strong> processes that occur in the presence of oxygen. In these processes,<br />

aerobic microorganisms oxidize bio-<strong>available</strong> organic and nitrogenous compounds. Removal of these oxygen demanding<br />

compounds provides a means to reduce odor emission and to reduce ammonia emissions. Aerobic <strong>treatment</strong> has not been<br />

used much in <strong>treatment</strong> of liquid or slurry <strong>manure</strong> primarily due to the relation between the benefits and the extra costs<br />

associated with operating the motors, compressors or fans required to supply enough oxygen to support aerobic bacteria.<br />

Several types of aeration of slurry were tested.<br />

Aeration may be partly to convert ammonia to nitrate, which can subsequently be trans<strong>for</strong>med into free N by denitrification,<br />

partly to reduce levels of organic matter in the liquid fraction. Nitrification (conversion of ammonia to nitrate) is very energyintensive<br />

in terms of power consumption <strong>for</strong> aeration, stirring, etc. If nitrate subsequently is converted into free N by<br />

denitrification a portion of the organic material in the slurry will be consumed. N and organic matter is lost in the process, and<br />

at the same time significant amounts of energy are consumed. The amount of aeration needed (in increasing order) depends<br />

on whether it is desired to just reduce odour, or completely remove the oxygen demand of the organic matter, or to supply<br />

enough oxygen <strong>for</strong> oxidation of ammonium to nitrate.<br />

See comments under composting –<br />

reference numbers 41 and 41A.<br />

Innovation stage<br />

Investment price, <br />

Basic Variable<br />

Operational<br />

costs,<br />

per tonnes<br />

per kg saved N<br />

or P leaching<br />

Complexity of<br />

implementation<br />

Research<br />

Pilot<br />

Practice <br />

Low – can be per<strong>for</strong>med without existing pumps, equipment and<br />

machinery on the farm<br />

Probably < <br />

1 per ton<br />

Major references Condition <strong>for</strong> leaching reduction effect Certainty of in<strong>for</strong>mation<br />

Foged, 2009 Scenarios II - V<br />

Prices High<br />

Effect on leaching High<br />

Depends on the<br />

situation of the<br />

individual farm.<br />

Low.<br />

74<br />

74

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