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

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228<br />

over several years so there will be an offset in the use and production,<br />

import and export balance over time.<br />

In some industries the solvents are consumed in the process, e.g. in the<br />

graphics and plastic industry, whereas in the production of paints and<br />

lacquers the solvents are still present in the final product. These products<br />

can either be exported or are used domestically. In order not <strong>to</strong><br />

double count consumption amounts of NMVOCs it is important <strong>to</strong> keep<br />

track of <strong>to</strong>tal solvent use, solvents not used in products and use of solvent<br />

containing products. Furthermore some chemicals may be represented<br />

as individual chemicals and also in chemical groups, e.g. “oxylene”,<br />

“mixture of xylenes” and “xylene”. Some chemicals are better<br />

inven<strong>to</strong>ried as a group of NMVOCs rather than individual NMVOCs,<br />

due <strong>to</strong> missing information on use or emission for the individual<br />

NMVOCs. The <strong>Danish</strong> <strong>inven<strong>to</strong>ry</strong> considers single NMVOCs with a few<br />

exceptions.<br />

Activity data for chemicals are thus primarily calculated from Equation<br />

1 with input from StatBank DK (2008). When StatBank (2008) holds no<br />

information on production, import and export or when more reliable information<br />

is available from industries, scientific <strong>report</strong>s or expert<br />

judgements the data can be adjusted or even replaced.<br />

(PLVVLRQ IDFWRUV<br />

For each chemical the emission is calculated by multiplying the consumption<br />

with the fraction emitted (emission fac<strong>to</strong>r), according <strong>to</strong>:<br />

<strong>Emission</strong> = consumption * emission fac<strong>to</strong>r<br />

The present <strong>Danish</strong> method uses emission fac<strong>to</strong>rs that represent specific<br />

industrial activities, such as processing of polystyrene, dry cleaning etc.<br />

or that represent use categories, such as paints and detergents. Some<br />

chemicals have been assigned emission fac<strong>to</strong>rs according <strong>to</strong> their water<br />

solubility. Higher hydrophobicity yields higher emission fac<strong>to</strong>rs, since a<br />

lower amount ends in waste water, e.g. ethanol (hydrophilic) and turpentine<br />

(hydrophobic).<br />

<strong>Emission</strong> fac<strong>to</strong>rs are categorised in four groups in ascending order:<br />

• Lowest emission fac<strong>to</strong>rs in the chemical industry, e.g. lacquer and<br />

paint manufacturing, due <strong>to</strong> emission reducing abatement techniques<br />

and destruction of solvent containing waste.<br />

• Other industrial processes, e.g. graphic industry, have higher emission<br />

fac<strong>to</strong>rs.<br />

• Non-industrial use, e.g. au<strong>to</strong> repair and construction, have even<br />

higher emission fac<strong>to</strong>rs.<br />

• Diffuse use of solvent containing products, e.g. painting, where practically<br />

all the NMVOC present in the products will be released during<br />

or after use.<br />

For a given chemical the consumed amount can thus be attributed with<br />

two or more emission fac<strong>to</strong>rs; one emission fac<strong>to</strong>r representing the<br />

emissions occurring at a production or processing plant and one emission<br />

fac<strong>to</strong>r representing the emissions during use of a solvent contain-

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