Eksempler på brug af Impact potentials på Engelsk og deres oversættelser til Dansk
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Colloquial
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Official
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Medicine
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Financial
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Ecclesiastic
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Official/political
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Computer
The normalised and weighted impact potentials are shown in Table 11.2.
In addition, the contribution of NOx is now included in the impact potentials.
This recommendation is valid for impact potentials in Denmark as well as in EU-15.
For impact potentials located outside Denmark and Europe the global reference is recommended.
The EU-15 normalisation reference is recommended for impact potentials located in Denmark and in Europe.
Folk også translate
The case, an LCA of a refrigerator, is presented in short in Chapter 11,including the figures for impact potentials.
Disposal phase Credit of impact potentials due to exploitation of energy from incineration, approx.
The European weighting factor is recommended as default value for impact potentials located in Denmark.
For regional impact potentials like nutrient enrichment, the EU-15 normalisation reference and the EU-15 weighting factor are recommended.
The European weighting factor is recommended as default value for impact potentials located in Denmark.
For impact potentials located in Denmark the EU-15 normalisation reference combined with the EU-15 weighting factor for photochemical ozone formation are recommended.
This means that the production phase has a net negative contribution to ecotoxicity andpersistent toxicity impact potentials.
The EU-15 weighting factors are recommended for impact potentials located outside Europe or at an unknown locality.
The impact potentials of these sub categories must be aggregated prior to weighting to allow use of the default EDIP97 weighting factors based on distance to political targets.
In this phase, electricity consumption again represents the main part of the impact potentials. Especially the yarn manufacturing process is energy-intensive.
Knitting 6% Credit of impact potentials due to recycling options in this process Credit of impact potentials due to recycling options in this process.
Introduction Lifecycle assessment is a method for identification andevaluation of environmental impact potentials of a product or a service from cradle to grave.
Based on impact potentials for human toxicity for the product in question the normalised and weighted impact potentials can be calculated for different media.
Weighting factors have not been established worldwide; the European weighting factors are recommended for impact potentials located outside Europe or at unknown locality.
The impact potentials in connection with wash of the work jacket primarily originate from detergents in washing agents, which result in potential human and persistent toxicity.
Weighting factors have not been established worldwide; the European weighting factors are recommended for impact potentials located outside Europe or at unknown locality.
The normalised as well as weighted impact potentials are calculated by using global and EU-15normalisation references and weighting factors, according to the general recommendations.
Obviously, the impacts from most upstream processes are located outside Denmark, while the impact potentials from the use and disposal stages primarily are located in Denmark.
Knitting 6% Credit of impact potentials due to recycling options in this process Credit of impact potentials due to recycling options in this process Pre-treatment Approx.
Weighting factors have only been established for human toxicity via soil for Europe;the European weighting factor is recommended as default value for impact potentials located in Denmark.
The site-generic ecotoxicity impact potentials are calculated using these factors in combination with the relevant EDIP97 characterisation factors for ecotoxicity from Wenzel et al.
Human toxicity is considered as a local as well as a regional impact and the EU-15 normalisation reference andweighting factors are recommended for impact potentials located in both Denmark and Europe.
Environmental impact potentials Environmental impact potentials related to toxicity Of the three environmental impact categories, the ones related to toxicity are dominant see figure 3.5.
For new studies,the site-generic form of EDIP2003 should be preferred due to the higher environmental relevance of its impact potentials, and because it offers the possibility of quantifying spatial variation.
The EDIP2003 photochemical ozone formation impact potentials are improved in two aspects compared to the impact potentials calculated using the EDIP97 characterisation factors;