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D-02 Reuse – water consumption

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Aspect D-02 Reuse – water consumption
Description
 There are different quality levels of water – freshwater, rainwater, greywater and waste water. Depending on these quality levels water, can be used for different applications (e.g. rainwater for washing clothes). How and under what circumstances is it possible to obtain benefits from the reuse of water?

related study objective

 ☒ stand-alone LCA ☒ comparative assertion

related study phase

 ☒ ☐ ☐ ☐ ☐
goal and scope definition inventory analysis (LCI) impact assessment (LCIA) interpretation reporting

relevant for
new buildings existing buildings construction products screening LCA simplified LCA complete LCA
Provisions Module D looks at the loads and benefits of the net output flow, if relevant and available. If water outputs or any output flow at EoL (not production waste) are reused, then to calculate the net output flow, any use of similar reused water or material as an input in Modules A1–C4 must be considered to calculate the net flow (output − input = net output flow).If there is a net output flow, then the impacts associated with any reuse processes after the ‘end-of-waste state’ can be included in Module D, together with a credit associated with the avoided production of the virgin product.
Rules from:

EN 15978

 7.4.6 Boundary for the benefits and loads beyond the system boundary (Module D)

EN 15804

 6.2.7 D Benefits and loads beyond the system boundary, information module

ILCD

 Not mentioned
Guidance

If any water from the building is reused outside the building, then the benefits of this use (credit for virgin water extraction and treatment, together with any impacts from the system boundary before substitutive use) are included in Module D.

If a waste material or waste energy is recycled, then the impacts associated with any processes after the ‘end-of-waste state’ before it can be used to substitute primary material can be included in Module D , together with a credit associated with the production of the virgin product it substitutes.

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D-03 Credits for recycling and energy recovery

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Aspect D-03 Credits for recycling and energy recovery
Description
 How should credits for recycling and energy recovery be allowed for?

related study objective

 ☒ stand-alone LCA ☒ comparative assertion

related study phase

 ☒ ☐ ☐ ☐ ☐
goal and scope definition inventory analysis (LCI) impact assessment (LCIA) interpretation reporting

relevant for
new buildings existing buildings construction products screening LCA simplified LCA complete LCA
Provisions Where recycled material or energy recovered at end of life are also used in the production of products (A1–A3), in Modules B1–B5 or C1–C4, then the net output flow is calculated as total output − total input.If there is a net output flow that provides benefits beyond the system boundary (as it produces material or energy that substitutes for virgin production), then the processes beyond the system boundary required to produce the recycled material or recovered energy substituted can be provided in Module D, together with a credit calculated by deducting the impact of producing the material or energy from virgin resources. For materials, this will be the virgin production route. For energy, this will be the use of the typical energy mix for heating (for heat energy) or the grid mix (for electrical energy), excluding secondary energy. In practice, unless energy from waste is a significant part of the energy or grid mix, the national mix can be used.
Rules from:

EN 15978

 7.4.6 Boundary for the benefits and loads beyond the system boundary (Module D)
8.8 Scenarios for benefits and loads beyond the system boundary – Module D

EN 15804

 6.2.7 D Benefits and loads beyond the system boundary, information module

ILCD

 Not mentioned
Guidance
 If the recycled product cannot substitute the primary product completely (e.g. it has 95% of the relevant functional equivalence), a justified value correction factor should be used to reflect this in the credit calculation.If waste is burned with less than 60% energy recovery, it has to be classified as a disposal process rather than a recovery process, and the process must be reported in Module C4. There may still be benefits for the production of energy beyond the system boundary that can be shown in Module D (as with landfilling and the recovery of gas from landfilling).

For example, if there was a net output flow of electricity, then the grid mix of electricity (excluding any secondary energy sources) should be used to credit the flow.

Note that the incineration of waste (i.e. material that is considered waste because it has not reached the end-of-waste state) may also be more efficient than 60%, but it must still be considered as a disposal process.

Back to 7 Aspects concerning Module D

9 Aspects concerning Module D – Benefits and loads beyond the system boundary

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This chapter addresses aspects that are related to life cycle stage D. All the aspects of this chapter provide provisions, rules and guidance for the goal and scope definition and the inventory analysis steps according to [ISO 14040] and [ISO 14044].

Module D makes it possible to quantify the reuse, recovery and recycling potential of a building or a building product. This module may be of interest in assessing and comparing designs for dismantling, or designs for recycling alternatives.

The following list describes the addressed aspects in Module D.

10 Discussions and perspectives

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In this chapter some of the findings of the project are discussed, connections to other research projects are made, and possible future developments of the EeBGuide guidance document are addressed.

The original aim of the EeBGuide project was not to develop new provisions or even standards for LCA, but to summarize existing provisions from the European standards and the ILCD Handbook, and give guidance on important LCA topics. This guidance is based on the latest LCA practitioners’ experience, and on findings from the EeBGuide project partners’ research and development activities, as well as from other European research projects. LCA practitioners now have a document that gives provisions for and guidance on the critical and most relevant aspects of conducting an LCA study for buildings and building products.

The EeBGuide project’s methodological approach was to combine both the CEN TC 350 and ILCD provisions. In this context, the guidance document remains as transparent as possible by linking to original rules from these reference documents and the chosen provision and guidance. The reference documents sometimes conflict. As far as possible, provisions from CEN TC 350 were applied, but if no provisions were given there, then the ILCD Handbook provisions were also considered (e.g. for consequential modelling). In some cases, both provisions (from CEN and ILCD) were considered, as they provide complementary rules that fulfil different goals and scopes for product or building LCAs (e.g. for the choice of environmental indicators). However, more work will be needed to analyse in greater detail the implications of ILCD provisions when applied to product and building LCA studies. The need for growing consistency between standards and ILCD documentation, however, was obvious throughout the project.

The EeBGuide guidance document is a new contribution to an existing set of documents providing operational guidance for building LCA studies. For example, two previous European research projects (LoRe-LCA and ENSLIC Building) can be also considered relevant sources of information for the LCA practitioner. They provide complementary guidance for some of the aspects covered in the EeBGuide. As far as possible, existing guidance from these projects was reported in the EeBGuide, e.g. by referring to online documentation or deliverables. However, not all of the aspects addressed in the EeBGuide guidance document were covered in these two previous European projects.

Indeed, the main innovation of the EeBGuide guidance document, compared with these previous projects, is to bring together  in a structured document some of the latest findings from the LCA and construction community. More than 150 aspects have been identified to be taken into account for a product or a building LCA. They are structured according to the LCA framework: i.e. goal and scope definition, inventory analysis, impact assessment, interpretation and reporting. This allows any LCA practitioner not necessarily aware of the specific wording of the CEN TC 350 standards to easily go through the document and identify the appropriate rules to follow. At the same time, the aspects are classified according to the life cycle stages of the EN 15804 and EN 15978 standards (Modules A, B, C and D). The provisions and guidance are broken down according to the study types (screening, simplified and complete LCA) so as to allow the practitioner to easily identify the main recommendations according to the stage of a project. The EeBGuide guidance document makes a distinction between stand-alone LCA and comparative assertions. This difference is very important, as comparative studies require more consistency to ensure that the results are not biased. The EeBGuide guidance document also distinguishes provisions for new buildings from those for existing buildings, as the LCA studies will not refer to the same goal and system boundaries. Reporting and review templates for case studies are also part of the guidance.

It is notable that some outcomes of the discussions of the EeBGuide project – within the consortium, with LCA experts, within the public consultation and with the review panel – proved relevant for the value of this document. Among the most important contributions to the general discussion of LCA in construction, the separation of operational guidance between product LCAs and building LCAs – and at the same time the assurance of consistency of these provisions – is one of the most relevant findings. In addition, the formulation of the concept of different study types – screening LCA, simplified LCA and complete LCA – in line with rules on when to apply which study type for what purpose, and how and what to include and exclude, reflects a common need of practitioners. The value of these concepts is given with the fact that the LCA community may now refer to uniform rules on how to conduct studies of the different types.

To summarise, the EeBGuide guidance document takes into account not only the latest findings of recent European projects and research and development works conducted at, for example CSTB (Environment department), Fraunhofer (IBP-GaBi department), PE International, the UNESCO Chair in Life Cycle and Climate Change at the University of Barcelona, and BRE Global, but also current provisions from the standards of CEN TC 350 and the ILCD Handbook. Finally, the EeBGuide guidance document is one of the first contributions at the European level towards a merging of relevant provisions from ILCD and CEN TC 350 in a consistent way. The EeBGuide partners believe that such a consistent guidance document provides a highly operational yet scientifically sound document for the building sector. The EeBGuide guidance document can now be used by the primary audience (LCA practitioners within E2B EI projects) and the secondary audience (building LCA tool developers and certification schemes).

As it is the first comprehensive contribution with the goal of merging diverging reference documents for different study types, the partners remain aware that many research topics still have to be conducted in the near future to support and more precisely specify the different definitions and guidance given as a first step in this guide. If there are any follow-on research projects in this direction, the results could be included in a new version of the EeBGuide. Also if there are new developments or outcomes from the standardization work or the ECO platform, these results will have to be incorporated in the guidance document as well. The EeBGuide guidance document has also identified issues that are not completely resolved when applying the CEN TC 350 standards. It may be a useful document for the standardization committee when revising the EN 15804/EN 15978 standards.

Further outcomes of more operational projects, such as the SBA Common Metrics project, have to be considered as very important contributions next to the EeBGuide guidance document to ensure comparability within different LCA studies. Future research projects should also focus on a common European reference building as a baseline scenario. Here, the most important parameters should be investigated (e.g. reference study periods, main EoL scenarios for materials, etc.) in order to define a European baseline scenario, providing average European values for its parameters, which will facilitate comparisons between research projects, and support the evolution of building labelling schemes.

List of abbreviations

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ADP abiotic depletion potential
ADPE abiotic resource depletion potential for elements
ADPF abiotic resource depletion potential of fossil fuels
AP acidification potential
BLBSB benefits and loads beyond the system boundary
BREEAM BRE Environmental Assessment Method
BWR basic work requirements
CML Centrum voor Milieukunde, Leiden (NL)
CPD Construction Products Directive
CPR Construction Products Regulation
CRU components for reuse
DGNB Deutsche Gesellschaft für Nachhaltiges Bauen (German Sustainable Building Council)
DSLT dynamic surface leaching test
E2B EI Energy-Efficient Building European Initiative
ECO European Construction Product Organization
EE exported energy per energy carrier
EMAS Eco-Management and Audit System Regulations
EoL end of life
EP eutrophication potential
EPBD Energy Performance of Buildings Directive
EPD Environmental Product Declaration
ESL estimated service life
ETAP Environmental Technologies Action Plan
FW use of net fresh water
GPP Green Public Procurement
GWP global warming potential (climate change)
HQE Haute Qualité Environmentale (French association and certification mark)
HWD hazardous waste disposed
IBU Institut Bauen und Umwelt e.V. (German EPD programme)
ID Interpretative Documents
ILCD International Reference Life Cycle Data System
IPP Integrated Public Policy
LCA life cycle assessment
LCC life cycle costing
LCI life cycle inventory (analysis)
LCIA life cycle impact assessment
LHV low heating value
MER materials for energy recovery
MFR materials for recycling
NHWD non-hazardous waste disposed
NPP net primary production
NRSF use of non-renewable secondary fuels
ODP ozone layer depletion potential
PCM phase change material
PCR Product Category Rules
PENRE use of non-renewable primary energy (excluding non-renewable primary energy resources used as raw materials)
PENRM non-renewable primary energy resources used as raw materials
PENRT total use of non-renewable primary energy resources
PERE use of renewable primary energy (excluding renewable primary energy resources used as raw materials)
PERM use of renewable primary energy resources used as raw materials
PERT total use of renewable primary energy resources
POCP photochemical ozone creation potential
ReqSL required service life
RSF use of renewable secondary fuels
RSL reference service life
RSP reference study period
RWD radioactive waste disposed
SBA Sustainable Building Alliance
SIP Sustainable Industrial Policy
SLP service life planning
SM use of secondary material

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[Lasvaux 2011] Lasvaux, S., Chevalier, J., Peuportier, B. ‘A data analysis tool to compare two LCA databases of construction materials used in building LCA applications for the French context’, Proceedings of the Life Cycle Assessment XI Conference, 4–6 October 2011, Chicago, USA, 11p.
[Lasvaux 2012] Lasvaux, S., Schiopu, N., Peuportier, B., Chevalier, J., ‘Relevance of a French simplified Life Cycle Inventory database using building products industry data’, Proceedings of the International Symposium on Life Cycle Assessment and Construction – Civil Engineering and Buildings, 10–12 July 2012, Nantes, France, 9p.
[Lebert 2012] Lebert, A., Lasvaux, S., Chevalier, J., Hans, J., ‘Environmental Performances of Buildings: identification of reference values through a statistical analysis’, Proceedings of the International Symposium on Life Cycle Assessment and Construction – Civil Engineering and Buildings, 10–12 July 2012, Nantes, France, 9p.
[Lemaitre 2009] Lemaitre, C., DGNB (Ed.): Nachhaltiges Bauen. DGNB Handbuch Neubau Büro- und Verwaltungsgebäude Version 2009. Stuttgart: DGNB 2009. ISBN: 978-3-942132-00-8.
[Leroy 2012] Leroy, C., Thomas, J-S., Avery, N., Bollen, J., Tikana, L. ‘Tackling recycling aspects in EN 15804’, Proceedings of the International Symposium on Life Cycle Assessment and Construction – Civil Engineering and Buildings, 10–12 July 2012, Nantes, France, 8p.
[LoRe-LCA 2011] LoRe-LCA: Low Resource consumption buildings and constructions by use of LCA in design and decision-making, European project (FP7), 2011, deliverables available online: http://www.sintef.no/ Projectweb/LoRe-LCA/Training/
[Lupsea 2012] Lupsea, M., Schiopu, N., Tiruta-Barna, L. Leaching of building products during their use stage: proposal for a reliable Life Cycle Inventory (LCI) of the released substances in water and soil. Proceeding of the international symposium on Life Cycle Assessment and Construction – Civil Engineering and Buildings, 10–12 July 2012, Nantes, France, 10p.
[Milà i Canals 2007] Milà i Canals, L., Bauer, C., Depestele, J., Dubreuil, A., Freiermuth Knuchel, R., Gaillard, G., Michelsen, O., Müller-Wenk, R., Rydgren B. ‘Key elements in a framework for land use impact assessment within LCA’, The International Journal of Life Cycle Assessment, volume 12, 2007.
[Nemry 2008] Nemry, F., Uihlein, A., Makishi Colodel, C., et al.: Environmental Improvement Potentials of Residential Buildings. (IMPRO-Building). (JRC Scientific and Technical Reports). Luxembourg: Office for Official Publications of the European Communities 2008. ISBN: 978-92-79-09767-6.
[Oers 2002] Oers, L. van, A. de Koning, J.B. Guinée & G. Huppes, ‘Abiotic resource depletion in LCA – Improving characterisation factors for abiotic resource depletion as recommended in the new Dutch LCA Handbook’, DWW report, Delft; available on: http://www.cml.leiden.edu/research/industrialecology/researchprojects/finished/abiotic-depletion-lcia.html
[Paulsen 2003] Paulsen, J. H., Borg, M.: A building sector related procedure to assess the relevance of the usage phase. The International Journal of Life Cycle Assessment 8 (2003) 3, pp. 142–150. Online: doi: 10.1007/BF02978459.
[Peuportier 2008] Peuportier, B. ‘Eco-conception des bâtiments et des quartiers’. Presse de l’Ecole des Mines de Paris, 2008. ISBN: 978-2-35671-001-7
[Pfister 2009] Pfister, S.; Koehler, A.M; Hellweg, Assessing the Environmental Impacts of Freshwater Consumption in LCA; Environ. Sci. Technol. 2009, 43, 4098–41042008
[Potting 2005] Potting, J. and Hauschild, M. ‘Background for spatial differentiation in life cycle impact assessment – the EDIP2003 methodology’, Environmental project no. 996, Danish Environmental Protection Agency, Copenhagen, 2005.
[Rosenbaum 2008] Rosenbaum, R.K., Bachmann, T.M., Gold, L.S., Huijbregts, M.A.J., Jolliet, O., Juraske, R., Köhler, A., Larsen, H.F., MacLeod, M., Margni, M., McKone, T.E., Payet, J., Schuhmacher, M., van de Meent, D., Hauschild, M.Z. ‘USEtox – The UNEP-SETAC toxicity model: recommended characterisation factors for human toxicity and freshwater ecotoxicity in Life Cycle Impact Assessment’ International Journal of Life Cycle Assessment, Volume 13, 2008.
[Solomon 2007] Solomon, S., Quin, D., Manning, M., et al. (Ed.): Climate change 2007. The physical science basis ; contribution of Working Group I to the Fourth Assessment Report of the Intergovernmental Panel on Climate Change. New York: UNEP 2007. ISBN: 978 0 521 88009 1.
[Van Caneghem 2010] Van Caneghem, J., Block, C., et Vandecasteele, C. ‘Assessment of the impact on human health of industrial emissions to air: Does the result depend on the applied method?’, Journal of Hazardous Materials, Volume 184, 2010.
[Van Zelm 2008] Van Zelm, R., Huijbregts, M.A.J., Den Hollander, H.A., Van Jaarsveld, H.A., Sauter, F.J., Struijs, J., Van Wijnen, H.J., Van de Meent, D. (2008). European characterization factors for human health damage of PM10 and ozone in life cycle impact assessment. Atmospheric Environment 42, 441–453.
[VROM 2007] VROM – Dutch Ministry of Spatial Planning Housing and the Environment. Soil Quality Decree (Netherlands), Decree of 22 November 2007 containing rules with respect to the quality of soil (Soil Quality Decree). Bulletin of Acts, Orders and Decrees of the State of the Netherlands, 34p, 2007.
[Waste directive 2008] European Union. Directive 2008/98/EC of the European parliament and of the council on waste and repealing certain directives. Off J Eur Union 2008;L312:3–30.
[WCED 1987] World Commission on Environment and Development: Our common future. Oxford: Oxford University Press 1987. ISBN: 019282080X.
[Weidema 1996] Weidema, B., et Wesnes, M. ‘Data quality management for life cycle inventories – an example of using data quality indicators’. Journal of Cleaner Production, Volume 4, 1996.
[Wittstock 2010] Wittstock, B., Fischer, M., Kreißig, J., et al.: The Role of LCA in the German Sustainable Building labelling. In: Hondo, H. (Ed.): EcoBalance 2010. The 9th International Conference on EcoBalance. Towards & Beyond 2020. Manuscripts. November 9–12, 2010. Tokio: ILCAJ 2010, pp. 81–82.
[Wittstock 2011] Wittstock, B., Braune, A., Fischer, M., et al.: LCA in Building labelling: Experiences from Germany. In: Finnish Association of Civil Engineers RIL, VTT Technical Research Centre of Finland (Ed.): SB 11 Helsinki. World Sustainable Building Conference. Oct. 18–21, 2011. Proceedings, vol. 1. Helsinki 2011, pp. 134–135.
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Annex A: Default Values.

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When conducting an LCA study, the practitioner is constantly confronted with figures: some are needed to specify a modelling parameter; others are needed as cross-references, or benchmarks for comparison purposes. Such numbers always depend on the context of a study, and are generally not globally valid, which is why this guidance does not specify the use of predefined default values.

For numerous studies, however, average or default values may be helpful, and have the potential to significantly reduce the effort for data collection, especially if the relevant figures are required, yet are not critical for the study outcome. Also, to gain confidence in one’s study, the practitioner may use such values for cross-reference. For such purposes, a non-comprehensive collection of various default values is provided in this Annex. This collection of values does not claim to be ultimately right, and the practitioner has to decide by himself or herself whether the given values are applicable to the study’s context, and whether utilizing these values will be beneficial for the study.

Default Parameters for Building LCA

Default Values – Buildings

Back to EeBGuide Guidance Document Part B: BUILDINGS

Reference Study Period: Buildings.

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Following a simplified understanding of a building’s life cycle, the reference study period can be seen as the timespan of use, i.e. the duration of services within Module B. Hence the reference study period has a significant impact on the use stage’s contribution to the life cycle impacts. This means that the reference study period influences the relation of impacts from the different life cycle stages, and thus may cause different conclusions to be drawn regarding the importance of a life cycle stage.

The following table provides definitions for reference study periods from various sources. These definitions are not based on scientifically proved lifetimes, but usually reflect a consensus, e.g. within one country.

Source Value Comments
Germany: building certification (DGNB) 50 years Default reference study period for all building types except for industrial buildings
Germany: building certification (DGNB) 20 years Reference study period for industrial buildings
Germany: building assessment (federal government) 30 years, 80 years Alternative values for scenario analyses
France 50 years, 100 years Commonly used reference study periods; no general definition available

 

Other default values

 

Annex B: Reference values for LCA indicators for buildings

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For referencing purposes, typical LCA results may be helpful. These values are typically heavily dependent on the assumptions made, and on the various rules that have been applied to a study. Hence a comparison with such values has to be made with special care.

Germany: DGNB

In Germany, the DGNB building labelling system defines benchmarks for the ‘physical part of the building’, i.e. the combination of building construction (Modules A1–A3), maintenance and refurbishment (Modules B2–B5) and the end of life (Modules C and D). All DGNB rules and provisions (e.g. reference study period) apply to allow for a justified comparison.

 

France: HQE Performance

The following tables present the results of a French pilot project, called HQE Performance, concerning the LCA of 74 low-energy buildings. The building LCA tool ELODIE has been used to perform the life cycle assessment of every case study. Results are presented as mean values calculated for the construction of new buildings for a 50-year reference study period.
The following building types are considered:

  • detached houses;
  • multi-residential buildings;
  • office buildings

Reference values are detailed for the following building impact sources:

  • equipment, products and materials (from cradle to grave, i.e. Modules A, B, C);
  • operational water consumption (Module B7);
  • operational energy consumption (thermal regulation uses, Module B6);
  • operational energy consumption (other uses, Module B6).

 

Reference values for new buildings

Note: The four indicators considered (non-renewable primary energy, global warming potential, inert waste and water consumption) are calculated according to the rules given in the French XP P01-020-3 and NF P01-010 standards.

Annex C: List of available references for life cycle impact assessment indicators chosen in EN 15804/EN 15978

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This Annex provides the practitioner with the sources of recommended LCIA methods (when they are in agreement with the EN 15804/EN 15978 standards). It also highlights the current inconsistencies between the units of the ILCD-recommended LCIA methods and the units of the EN 15804/EN 15978 standards.

The practitioner should notice that while different impact assessment methods are recommended by the ILCD Handbook or given in the EN standards, one cannot be sure that LCA data (both generic LCA background databases and EPDs) do support the application of an LCIA method. The practitioner has rather to evaluate data availability (among other decision criteria) before deciding on which impact methods to use.

Background information in EN 15804/EN 15978

The EN 15804 standard states that

“The impact assessment should be carried out for the following impact categories:

  • global warming
  • ozone depletion
  • acidification of land and water
  • eutrophication
  • photochemical ozone creation
  • depletion of abiotic resources (elements)
  • depletion of abiotic resources (fossil)

The characterization factors applied in the European Reference Life Cycle Database (ELCD) provided by the European Commission (DG Joint Research Centre – Institute for Environment and Sustainability) should be used and shall follow the respective updates of the ELCD [EN 15804]. In addition, the characterization factor for ADP (elements and fossil) shall be taken from CML (Institute of Environmental Sciences, University of Leiden, The Netherlands). The characterization factors for ADP-fossil fuels are the net calorific values at the point of extraction of the fossil fuels.”

References that can be considered for the impact category given in EN 15804/EN 15978

There is a need to specify the reference (scientific articles, scientific reports etc.) for each impact category, as the LCA practitioner can find several methods and characterization factors within one impact category (e.g. photochemical ozone formation). At the same time, the International Reference Life Cycle Data System (ILCD) has recently provided recommended methods for each impact category. It is proposed here to identify, for the EN 15804 impact categories, the available references and characterization factors that can be applied when using the EeBGuide.

Three reports were used to derive the references for LCIA indicators given in the EN 15804/EN 15978 standards.

– Analysis of existing Environmental Impact Assessment Methodologies for use in Life Cycle Assessment (First edition);

– Framework and requirements for Life Cycle Impact Assessment models and indicators (First edition);

– Recommendations for Life Cycle Impact Assessment in the European context (First edition, December 2010).

References of ILCD-recommended LCIA methods that may be used when applying the EeBGuide in the framework of EN 15804/EN 15978 impact categories

The first table presents the references of the ILCD recommended LCIA methods that could be used when applying the EeBGuide. A comment below the unit of the LCIA indicators indicates whether it is consistent with the unit given in EN 15804 and EN 15978.

 

Impact category in EN 15804

Parameter in EN 15804

Unit of LCIA indicator referring to method given in next column

Sources of recommended LCIA method based on ILCD Handbook

Global Warming

Global warming potential, GWP;

kg CO2 equiv

(compliance with the unit given in EN 15804/EN 15978)

 ILCD-recommended LCIA method: Climate change; midpoint; GWP100;

 

Source: Forster, P., Ramaswamy, V., Artaxo, P., Berntsen, T., Betts, R., Fahey, D.W., Haywood, J., Lean, J., Lowe, D.C., Myhre, G., Nganga, J., Prinn, R., Raga, G., Schulz, M. and Van Dorland, R., (2007). Changes in Atmospheric Constituents and in Radiative Forcing. In: Climate Change 2007: The Physical Science Basis IPCC 2007. Contribution of Working Group I to the Fourth Assessment Report of the Intergovernmental Panel on Climate Change.

Ozone depletion

Depletion potential of the stratospheric ozone layer, ODP

kg CFC 11 equiv

(compliance with the unit given in EN 15804/EN 15978)

 ILCD-recommended LCIA method: Ozone depletion; midpoint; ODP;

 

Source: World Meteorological Organization, 1999: Scientific assessment of ozone depletion: 1998. Global Ozone Research and Monitoring Project – Report no. 44. Geneva.)

Acidification for soil and water

Acidification potential of soil and water, AP;

moles H+ equiv

(no compliance with the unit given in EN 15804/EN 15978)

 ILCD-recommended LCIA method: Acidification terrestrial and freshwater; midpoint; Accumulated Exceedance

 

Source: Seppälä, J., Posch, M., Johansson, M., Hettelingh, J.P. (2006). Country-dependent Characterisation Factors for Acidification and Terrestrial Eutrophication Based on Accumulated Exceedance as an Impact Category Indicator. International Journal of Life Cycle Assessment 11(6): 403-416.

 

With updated characterization factors available in:

Posch, M., Seppälä, J., Hettelingh, J.P., Johansson, M., Margni M., Jolliet, O. (2008). The role of atmospheric dispersion models and ecosystem sensitivity in the determination of characterisation factors for acidifying and eutrophying emissions in LCIA. International Journal of Life Cycle Assessment (13) pp.477–486

 

Eutrophication

Eutrophication potential, EP

moles H+ equiv

(no compliance with the unit given in EN 15804/EN 15978)

 ILCD-recommended LCIA method: Eutrophication terrestrial; midpoint; Accumulated Exceedance;

 

Source: Seppälä, J., Posch, M., Johansson, M., Hettelingh, J.P. (2006). Country-dependent Characterisation Factors for Acidification and Terrestrial Eutrophication Based on Accumulated Exceedance as an Impact Category Indicator. International Journal of Life Cycle Assessment 11(6): 403-416.

With updated characterization factors available in:

Posch, M., Seppälä, J., Hettelingh, J.P., Johansson, M., Margni M., Jolliet, O. (2008). The role of atmospheric dispersion models and ecosystem sensitivity in the determination of characterisation factors for acidifying and eutrophying emissions in LCIA. International Journal of Life Cycle Assessment (13) pp.477–486

 

Other source: [Guinée 2001]

Photochemical ozone creation

Formation potential of tropospheric ozone, POCP;

kg Ethene equiv

(compliance with the unit given in EN 15804/EN 15978)

 ILCD-recommended LCIA method: Photochemical ozone formation; midpoint – human health; POCP;

 

Source: Van Zelm, R., Huijbregts, M.A.J., Den Hollander, H.A., Van Jaarsveld, H.A., Sauter, F.J., Struijs, J., Van Wijnen, H.J., Van de Meent, D. (2008). European characterization factors for human health damage of PM10 and ozone in life cycle impact assessment. Atmospheric Environment 42, 441–453.

 

Depletion of abiotic resources: elements

Abiotic depletion potential (ADP-elements) for non-fossil resources

kg Sb equiv

(compliance with the unit given in EN 15804/EN 15978)

 ILCD-recommended LCIA method: Resource depletion- mineral, fossils and renewables; midpoint; abiotic resource depletion; The ILCD Handbook recommends using the reserve base

 

Source:

ADP-elements based on an update of characterization factors for elements and additional characterization factors have been listed on the basis of USGS economic reserve and reserve base figures in addition to the ultimate reserve by:

Oers, L. van, A. de Koning, J.B. Guinée & G. Huppes, 2002. Abiotic resource depletion in LCA – Improving characterization factors for abiotic resource depletion as recommended in the new Dutch LCA Handbook. DWW report, Delft; see http://www.cml.leiden.edu/research/industrialecology/researchprojects/finished/abiotic-depletion-lcia.html

 

Depletion of abiotic resources: fossil fuels

Abiotic depletion potential (ADP-fossil fuels) for fossil resources

MJ, net calorific value

(compliance with the unit given in EN 15804/EN 15978)

 ILCD-recommended LCIA method: Resource depletion- mineral, fossils and renewables; midpoint; abiotic resource depletion;

 

Source:

ADP-fossil fuels based on low heating values (LHV) of the fossil fuels. The fossil fuels are considered to be fully substitutable. Factors provided by: Oers, L. van, A. de Koning, J.B. Guinée & G. Huppes, 2002. Abiotic resource depletion in LCA – Improving characterization factors for abiotic resource depletion as recommended in the new Dutch LCA Handbook. DWW report, Delft; see http://www.cml.leiden.edu/research/industrialecology/researchprojects/finished/abiotic-depletion-lcia.html

 

* CF are provided by [Oers 2002]

Link to online characterization factors of the ILCD-recommended LCIA methods that may be used when applying the EeBGuide in the framework of EN 15804/EN 15978 impact categories

MS Excel CF: http://lct.jrc.ec.europa.eu/assessment/resolveuid/cdfa2451af584ec3b3056a17060e4b6f (RAR-File)

ILCD formatted: http://lct.jrc.ec.europa.eu/assessment/resolveuid/0e0eb8ac1856f79a0a3816f20514b8db (ZIP-File)

 

References of other LCIA methods that may be used when applying the EeBGuide in the framework of EN 15804/EN 15978 impact categories

As for some ILCD-recommended LCIA methods, there is not a consensus with the standards (e.g. a different unit is proposed in the ILCD-recommended method). The practitioner can have a look at the online ILCD report for more information on the other LCIA methods:

http://lct.jrc.ec.europa.eu/assessment/LCIA-CF-09-02-2012-def.pdf

The CML 2002 LCIA method has also been very much used in practice for many years. The practitioner who would like to consult the online characterization factors can go to the following link:

http://cml.leiden.edu/software/data-cmlia.html

Please note that the units for AP and EP in the CEN TC 350 standards correspond to the CML 2002 LCIA method.

 

Concluding remarks:

A list of references for each impact category has been given, based upon the ILCD Handbook recommendations.

It should be kept in mind by the practitioner that there is still quite some freedom when applying the EeBGuide for different impact categories: acidification and eutrophication as the units (and thus the methods) differ between the EN 15804 standard and the ILCD recommend methods. In addition, some of the newly ILCD-recommended methods may not be implemented in commercial LCA software such as GaBi or SimaPro. Also, generic background databases and EPDs may not necessarily contain impact factors or indicator values for all of the methods listed. This situation, however, is expected to change and improve over time.