? |
Figure cannot be estimated due to lack of data. The flow in question
should be overlooked. |
x? |
Figure or some of the subfigures referred to is deemed highly uncertain. |
1. |
Reference is made to section 2.1.1 and section 2.1.3. |
2. |
Figures refer to brominated dioxins. Toxicity equivalency factors are
assumed similar to factors for chlorinated dioxins. |
3. |
The consumption figure covers consumption with clay and clay-like raw
materials used for manufacturing of insulation materials, tiles, bricks and similar items.
The dominant part of this consumption is assumed to be destroyed by manufacturing
processes. The indicated loss to waste covers dioxins in clay used for decoration and
educational purposes. |
4. |
The quantity stated under "other routes" covers dioxin in filter
dust sold as material for flue gas cleaning operations. |
5. |
The quantity stated under "other routes" covers dioxin in filter
dust exported for zinc recovery. An estimated < 0.016 g I-TEQ will be reused in asphalt
and cement manufacturing. |
6. |
The quantity stated under "other routes" covers dioxin in meat
and bone meal exported. |
7. |
The quantity stated as "consumption by products" is also
included in the consumption figure for feedstuff products. |
8. |
The quantity stated under "emission to soil" covers land
application of manure and similar waste products from animal and fish farming. As no
detailed investigation of dioxin circulation within the Danish animal and fish farming
sectors has been undertaken, the figure should be taken as a rough estimate only. |
9. |
The quantity stated under "other routes" covers dioxin paper and
cardboard collected for recycling. |