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Annual Danish informative inventory report to UNECE. Emission ...

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242<br />

Another important cause of the significant decrease in the NH3 emission<br />

since 1985 is changes in practice of manure application <strong>to</strong> the fields<br />

where considerable changes have taken place. From the beginning of<br />

the 1990s slurry has increasingly been spread using trailing hoses. From<br />

the late 1990s the practice of slurry injection or mechanical incorporation<br />

in<strong>to</strong> the soil has increased. This development is a consequence of a<br />

ban on broad spreading but it is also a consequence of the general requirement<br />

<strong>to</strong> improve the utilisation of nitrogen in the manure - e.g. requirements<br />

<strong>to</strong> a larger part of the nitrogen in manure has <strong>to</strong> be included<br />

in the farmers nitrogen accounting. This has forced farmers <strong>to</strong> consider<br />

the manure as a resource instead of a waste product.<br />

3DUWLFXODWH PDWWHU<br />

In NFR, the emission of particulate matter (PM) is registered for the<br />

years 2000 <strong>to</strong> 2009. The emission from the agricultural sec<strong>to</strong>r includes<br />

the emission of dust from animal housing systems, which include emission<br />

from cattle, pigs, poultry, horses, sheep and goats. Furthermore,<br />

the emission from field burning of agricultural wastes is calculated.<br />

Present, the <strong>Danish</strong> <strong>inven<strong>to</strong>ry</strong> do not include emission from plant production,<br />

which means activities related <strong>to</strong> field operations as harvesting<br />

and cultivation of the soil.<br />

TSP emission from the agricultural sec<strong>to</strong>r contributes 28 % <strong>to</strong> the national<br />

TSP emission in 2009 and the emission shares for PM10 and PM2.5<br />

are only 17 % and 4 % respectively. Most of this comes from animal<br />

production. The emission from the field burning of agricultural residues,<br />

contributes less than 1 % <strong>to</strong> the agricultural emission.<br />

The same emission fac<strong>to</strong>r is used for all years. So changes in the <strong>to</strong>tal<br />

PM emissions for each lives<strong>to</strong>ck category is mainly reflecting the<br />

changes in number of animal, but also effected by the distribution of the<br />

subcategories and changes in the housing type.<br />

The PM emission from agricultural activities, given in TSP, has decreased<br />

from by 10 % which is mainly due <strong>to</strong> a fall in the emission from<br />

swine (Figure 6.2). A decrease in emission from swine is a result of<br />

changes in housing system <strong>to</strong>wards slurry based systems, which has a<br />

lover emission fac<strong>to</strong>r than solid based system. Another reason is<br />

changes in the fraction of subcategories. An increase in production of<br />

weaners has taken place from 2000-2009 and upper site situation for fattening<br />

pigs, where the emission fac<strong>to</strong>r is higher.

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