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Tålegrænser for lufforurening - DCE - Nationalt Center for Miljø og ...

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Responses<br />

The use of critical<br />

loads/levels in strategic<br />

planning<br />

Discussion<br />

14<br />

agricultural crops and trees and relatively little in<strong>for</strong>mation is available<br />

on the response of natural vegetation to ozone. The Average<br />

Above Threshold (AOT) is the sum of critical time (hours) multiplied<br />

by the exceedance of the critical level of e.g. 40 ppb (AOT40)which<br />

has been demonstrated to damage agricultural crops and trees. But<br />

plants react to ozone fluxes rather than concentrations and there<strong>for</strong>e<br />

this criteria is being debated.<br />

DEM can run various scenarios to analyse the relations between<br />

emissions of ozone precursors and critical level exceedances of<br />

ozone. Calculation of consequences of reductions of NO x and VOC<br />

emissions in all European countries and combinations of the two reactants<br />

are carried out. Output scenarios are coupled to the tree<br />

growth model TREGRO to evaluate the effects on tree vegetation and<br />

to separate ozone effects from other stress.<br />

The Danish work on integrated assessment of air pollution is being<br />

built on a number of models in a chain of interactions. At present<br />

only rather preliminary model interaction has been carried out, but<br />

some realistic scenarios will be produced in near future. Internationally,<br />

the RAINS model is used to prepare scenarios <strong>for</strong> negotiations<br />

<strong>for</strong> the coming Acidification Strategy <strong>for</strong> EU and <strong>for</strong> the Multipollutant/Multi-effect<br />

protocol under the Geneva Convention.<br />

RAINS consist of 5 Alements: 1) Energy and agricultural scenarios, 2)<br />

Emission inventories, 3) Transport matrices, 4) Critical loads and levels<br />

and 5) Abatement costs. The resulting optimisation process calculates<br />

the cost-effective way to achieve the environmental targets.<br />

The critical loads and levels <strong>for</strong> ecosystems and plants are being used<br />

internationally <strong>for</strong> strategic planning. These scenarios and negotiations<br />

result in fixed emission ceilings <strong>for</strong> SO 2, NO x and NH 3 <strong>for</strong> each<br />

country in the <strong>for</strong>thcoming Acidification Strategy. The implementation<br />

of necessary abatement measures will be very costly <strong>for</strong> Denmark<br />

and there is an urgent need to establish an Integrated Assessment<br />

System <strong>for</strong> the analysis of how to distribute these ceilings<br />

among different sectors in Denmark.<br />

From the base model ADAM satellite models have to be developed to<br />

run scenarios <strong>for</strong> energy, transport and agricultural sectors. This in<strong>for</strong>mation<br />

is crucial as starting point <strong>for</strong> such calculations. The calculation<br />

and mapping of critical loads is another important end of the<br />

chain: what will be the resulting exceedances of critical loads and<br />

levels <strong>for</strong> Danish and European ecosystems? Cost optimisations will<br />

be needed to analyse which sector can contribute most efficiently to<br />

achieve the emission goals <strong>for</strong> the year 2010.<br />

The problems, their causes and solutions are indeed complex and<br />

much ef<strong>for</strong>t has been spent on enabling the critical loads/levels concept<br />

to be a fundamental criteria <strong>for</strong> such analysis. A number of uncertainties<br />

are found at each element and at each scale of analysis, but<br />

the endpoint is that consistent calculations over more than a decade<br />

have shown the same general patterns of air pollution. The effects of<br />

implementation of the resulting conventions are now being seen as<br />

well.

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