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ILCD Handbook: Framework and requirements for LCIA models and ...

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<strong>ILCD</strong> <strong>H<strong>and</strong>book</strong>: <strong>Framework</strong> <strong>and</strong> <strong>requirements</strong> <strong>for</strong> <strong>LCIA</strong> <strong>models</strong> <strong>and</strong> indicators First edition<br />

ACIDIFICATION Check the following:<br />

Overall evaluation of stakeholders acceptance criteria<br />

Final recommendation<br />

4.8 Eutrophication<br />

4.8.1 <strong>Framework</strong> <strong>and</strong> scope<br />

Threshold<br />

(Minimum<br />

score)<br />

Importance<br />

(H-N)<br />

The impact category appears under different names like eutrophication, nutriphication or<br />

nutrient enrichment. It addresses the impacts from the macro-nutrients nitrogen <strong>and</strong><br />

phosphorus in bio-available <strong>for</strong>ms on aquatic <strong>and</strong> terrestrial ecosystems.<br />

In natural terrestrial systems, the addition of nutrients may change the species<br />

composition of the vegetation by favouring those species which benefit from higher levels of<br />

nutrients to grow faster than more nutrient efficient plants. This there<strong>for</strong>e changes the plant<br />

community from nutrient-poor (e.g. heath l<strong>and</strong>s, dunes <strong>and</strong> raised bogs) to nutrient rich <strong>and</strong><br />

more commonly, due to the widespread dispersion of nutrients,, plant communities. The<br />

primary impact on the plant community leads to secondary impacts on other species in the<br />

terrestrial ecosystem. Terrestrial eutrophication is caused by deposition of airborne<br />

emissions of nitrogen compounds like nitrogen oxides (NOx = NO <strong>and</strong> NO2) from combustion<br />

processes <strong>and</strong> ammonia, NH3 from agriculture. Airborne spreading of phosphorus is not<br />

prevalent, <strong>and</strong> terrestrial eutrophication is there<strong>for</strong>e mainly associated with nitrogen<br />

compounds.<br />

In aquatic systems, the addition of nutrients has a similar primary impact by fertilising the<br />

plants (algae or macrophytes) with a number of consequences <strong>for</strong> the ecosystem:<br />

Species composition of the plant community changes to more nutrient-dem<strong>and</strong>ing<br />

species;<br />

Algal blooms create shadowing, filtering the light penetrating into the water mass,<br />

changing life conditions from the macrophytes, which need the light <strong>for</strong> photosynthesis,<br />

<strong>and</strong> <strong>for</strong> predatory fish which need the light to see <strong>and</strong> catch their prey;<br />

Oxygen depletion near the bottom of the water body where dead algae deposit <strong>and</strong><br />

degrade.<br />

All these consequences lead to a change in the species composition <strong>and</strong> of the function of<br />

the exposed aquatic ecosystem.<br />

In aquatic systems it is often one of the macronutrients which limits the growth of algae.<br />

Addition of the limiting nutrient will lead to increased primary production, while addition of the<br />

nutrient which is not limiting will have no effect on the primary production, <strong>and</strong> this should be<br />

reflected in the life cycle impact assessment. There may be seasonal variations in the pattern<br />

of limiting nutrients, but as a general rule, P is the limiting nutrient in freshwater systems<br />

while N is limiting nutrient in marine systems.<br />

Freshwater <strong>and</strong> marine aquatic systems are exposed to water-borne emissions (nitrate,<br />

other nitrogen compounds expressed as total N, phosphate <strong>and</strong> other phosphorus-containing<br />

compounds expressed as total P). Marine aquatic systems <strong>and</strong> very large lakes are also<br />

substantially exposed by airborne emissions (NOx).<br />

4 Requirements <strong>for</strong> specific impact categories 61

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