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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 />

concept. For biodiversity, the species-diversity oriented PDF-concept is seen as the only<br />

really operational concept among those investigated, integrating the potentially lost fraction<br />

of natural species over area <strong>and</strong> time.<br />

3.2.2 Background <strong>and</strong> Discussion<br />

The Area of Protection ‗Natural Environment‘ (or Ecosystem Health), encompasses the<br />

natural ecosystems globally, in terms of their function <strong>and</strong> structure. It ought to be noted that<br />

the resource aspect of ecosystems (biological renewable resources, <strong>and</strong> managed, manmade<br />

ecosystems like plantations or agricultural fields) is addressed under the AoP ‗Natural<br />

Resources‘ <strong>and</strong> not included here. For Natural Environment, the aim is to quantify the<br />

negative 11 effects on the function <strong>and</strong> structure of natural ecosystems as a consequence of<br />

exposure to chemicals or physical interventions 12 .<br />

The complexity of the natural ecosystems with their multiple interactions between different<br />

populations at the same or different trophic levels, <strong>and</strong> the physical <strong>and</strong> chemical<br />

surroundings makes it a challenging task to assess effects on their structure <strong>and</strong> functions. In<br />

ecotoxicology, this task has typically been addressed by focusing on the occurrence of<br />

different species in the ecosystem, i.e. the biodiversity.<br />

―Biodiversity can be defined at different levels: ecological diversity (ecosystems),<br />

population diversity (species) <strong>and</strong> genetic diversity (genes). This grouping is reflected in the<br />

Rio Convention‘s definition of biodiversity as ―the variability among all living organisms from<br />

all sources, including inter alia, terrestrial, marine <strong>and</strong> other aquatic ecosystems <strong>and</strong><br />

ecological complexes of which they are part; this includes diversity within species, between<br />

species <strong>and</strong> of ecosystems” (EEA, 1997).<br />

“Biodiversity, which is an indicator of the ecosystem structure, does not automatically<br />

reflect the natural environment (Forbes <strong>and</strong> Forbes 1993; Tillman 2001). This is due to the<br />

fact that the integrity of ecosystems depends not only on species richness (<strong>and</strong> other<br />

structure related properties, e.g. number of trophic levels) but also on the protection of the<br />

function of the ecosystem (e.g. biomass production <strong>and</strong> nutrient cycling). If <strong>for</strong> example a<br />

chemical stress is targeted at a single species but this species is a keystone species on<br />

which the function of the ecosystem heavily relies, the function of the ecosystem may<br />

undergo major changes,” 13 whereas other species may exert functions which are easily taken<br />

over by other species, should this species disappear (Mooney et al., 1995).<br />

When modelling damage to natural ecosystems, biodiversity is thus not the only possible<br />

endpoint. Function-related parameters like biomass production or mineralisation might<br />

represent better the functional per<strong>for</strong>mance of the ecosystem <strong>and</strong>, in some cases, might be a<br />

more relevant endpoint indicator, depending on which properties of the AoP are deemed<br />

worthy of protection 14 . Recreative value may thus be better represented by a biodiversity<br />

indicator, whereas production value <strong>and</strong> life support functions may be better represented by<br />

11 All impacts on the environment are considered as negative in the sense of being undesirable. To the<br />

extent that the product system, which is the object of the LCA, has positive impacts on the<br />

environment (e.g. wastewater treatment), this is quantified in the inventory analysis.<br />

12 The following midpoint impacts are considered to contribute to damages on Natural Environment,<br />

although the contribution has not <strong>for</strong> all of them been modelled by recommended methods: climate<br />

change, ozone depletion, photochemical ozone <strong>for</strong>mation, ionising radiation, acidification,<br />

eutrophication, ecotoxicity, l<strong>and</strong> use, desiccation <strong>and</strong> salination.<br />

13 From J. Payet & H.F. Larsen, Damage modelling <strong>for</strong> Life Cycle Impact Assessment on Ecosystems;<br />

Report- Swiss National Fund <strong>and</strong> Ecole Polytechnique Fédérale de Lausanne; November 2002 (13p.).<br />

14 The health of Earth ecosystems <strong>and</strong> the role of ecosystem function <strong>for</strong> quality of human life is<br />

investigated <strong>and</strong> extensively discussed in the Millenium Ecosystem Assessment – see<br />

http://www.millenniumassessment.org/en/index.aspx<br />

3 Requirements <strong>for</strong> Areas of Protection 20

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