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Author: Anh-Migrate

Reference Study Period: Buildings.

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

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

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.

 

2.4.1. How to commence and proceed with an LCA study

This document yields several distinctions that are relevant for the further procedure to compile an LCA study. The distinctions are given in the decision tree showed in Figure 5.

In the first step, both for a building LCA and a product LCA, the decision on the scope of the study has to be made. This leads to the definition of the study type used and the relevant aspects to assess may be filtered accordingly for the next steps. This includes the identification of life cycle stages that should be assessed and those that will remain optional. Refer to Table 3 for the identification of mandatory and optional life cycle stages.

On the basis of the study type chosen and the life cycle stages of concern, the remaining relevant aspects are then taken into account during the setup of the LCA building model and for defining individual parameters of the system.

As the term “energy efficiency” implies a lower energy input into a building or building service through a more advantageous benefit/input ratio, a comparison of the situation with or without the technology concerned may be required to identify the actual environmental consequences of utilizing such a technology. It needs to be noted that the careful definition of the two situations and a comprehensive life cycle view (inclusion of all relevant life cycle stages) is necessary to cover all environmental consequences. In addition, comparison should be done on the basis of a common functional equivalent (i.e. a representation of the required technical characteristics and functionalities of the building).


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2.4.2. LCA study setup: Generic template

After the selection of the study type and the subsequent filtering of aspects, the LCA study is set up according to the general LCA practice as resulting from applying ISO 14040/14044. This process is briefly explained with a generic template of how to set up an LCA study. The individual steps are numbered – note that this numbering does not relate to any study or other procedure that is defined elsewhere.

Step 1 – Goal and Scope definition

The definition of goal and scope mainly relates to the identification of study type and aspects considered for the LCA study as described in section 2.4.1. Based on the definition of reasons for carrying out the study as well as its intended application and audience, further specifications have to be made, e.g.:

  • Object of assessment (e.g. building or innovative technology) and its function (e.g. office use or energy producing façade collector)
  • Set up of a functional equivalent – special especially important for comparative assertions
  • System boundaries – specifications on life cycle phases to be included (e.g. for existing buildings) depending on the study type or hints for applying cut-off rules (e.g. with regard to infrastructure and transport) are specified
  • Procedure for allocation – several common allocation cases (e.g. for co-production or reuse and recycling) with regard to mass, energy or environmental significance are provided
  • Choice of environmental impact categories, indicators and characterization models used for the impact assessment
  • Data requirements and quality – the type of data to be used (e.g. generic or specific), data uncertainty, the use of foreground or background data (e.g. power-mix) and specific requirements on data quality for comparative assertions are defined; missing data have to be documented
  • Assumptions and limitations – may address e.g. the setup of specific scenarios for the use phase, the treatment of capital equipment or machinery within the production phase, or deviations from guidance provided within this document; a transparent documentation is required

Examples and guidance on the mentioned topics are provided within respective aspects of the chapters for “Goal and Scope definition”.

Step 2 – Inventory Analysis and Product Model

The way of data collection as well as the quantification of input and output flows (e.g. materials or energy) differs for screening, simplified and complete LCA studies and depends on the level of separating single elements for the object of assessment as well as the assessed life cycle stages . Data sources (e.g. public available or company/product specific ones) used and the quality of background data for the inventory analysis have an influence on the impact assessment. Guidance on data collection, calculation, validation and relating the information to e.g. life cycle stages or elements of the object of assessment is provided within the chapters for “Life cycle inventory analysis”. Furthermore, building and building product contributors are defined which have to be considered.

Step 3 – Impact Assessment

For the quantification of potential environmental impacts, the choice of environmentally relevant, technical and scientifically valid environmental indicators as well as the underlying characterization models for impact assessment, is of importance. Environmental indicators and impact categories where scientific consensus is not yet reached so far (e.g. water consumption, land use change or carbon sequestration) are addressed within the chapters for “Life Cycle Impact Assessment”.

Step 4 – Interpretation and Documentation

The interpretation of results serves e.g. for identifying hot spots (e.g. distinct life cycle phases or elements of the object of assessment contributing to environmental impacts) or understanding sensitivity and uncertainty of results through respective analysis. Requirements and guidance on the use of normalization, grouping or weighting are provided within the chapters for “Interpretation”. Cases, where a sensitivity analysis is useful, are defined as well.

Reporting templates are provided online at the official project website (https://www.generis-solution.eu/) and assist especially in conducting step 1. These templates form the basis for a documentation which is in-line with the present guidance document and which might be enhanced with further specific information, if required or recommended (e.g. if future technologies and innovations are regarded at).

Step 5 – Review

An external critical review is necessary for all comparative LCA studies or studies which are made public available. Guidance on simplifications for the review of stand-alone or screening LCA studies or studies within the E2B EI is provided under section “Reporting” within chapter “General aspects”.


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2.4.3. Use of a baseline scenario

Several of the aspects addressed in this guidance define a ‘standard set of parameter values’ for a study, e.g. a default reference study period. This standard set of parameter values is denoted as baseline scenario and provides a basis that allows for comparisons between different studies, e.g. two building LCA studies. The baseline scenario generally contains the definitions and parameter value choices from EN 15804 (products) and EN 15978 (buildings).

Additionally, standard values for a parameter frequently contain options to explore the implications of different choices (e.g. reduced or extended reference study periods). If such deviations are chosen, sensitivity analysis has to be undertaken to compare the new scenario against the baseline scenario in order to explore the influence of the parameter value on the results. Then, results with the use of the default parameter value (baseline scenario) and with modified parameter values (assessed situation) should be compared.

The baseline scenario (i.e. standard set of parameter values) contains the following provisions:

Table 4: Standard set of parameter values for the baseline scenario

Aspect

Parameter

Standard parameter value

G- 04. “Reference study period”

Reference study period

50 years

G- 10. “Future technical developments and innovation”

Consideration of innovation

No innovation to be considered, current technologies to be used

G- 12. “Accounting for carbon storage / carbon sequestration”

Carbon storage

Carbon storage is not considered

G- 25. “Water consumption”

Scarcity of water

Not scarcity of water to be considered

A- 03. “Transportation of products to the construction site” – screening and simplified LCA”

Transport distance

293 km

A- 04. “Transportation of products to the construction site – Complete LCA”

Transport distance

293 km

B- 03. “Transport of people”

Transport of people

No transport of people to be considered

B- 13. “Replacement frequency”

Full numbers of replacement cycles or partial cycles

Replacement in whole number cycles

B- 20. “Electricity consumption in dynamic LCA data”

Electricity consumption

Annual average data sets for electricity

B- 25. “Operational energy demand – Consideration of user behavior for stand-alone or comparative LCA of new buildings”

User behavior

No user behavior to be considered

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A- 22. “Packaging waste”

Aspect A- 22. “Packaging waste”
Description
What and how to allow 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 A5 should include the processing of the waste from product packaging in complete LCA studies, unless in falls under cut-off rules.
Rules from:
EN 15978:8.5 Scenarios for the construction process stage (Modules A4-A5)

EN 15804:

6.2.3 A4-A5, Construction process stage, information modules

Guidance
Cut-off rules may apply and it should be noted that for most construction projects, this aspect is likely to fall under the cut-off-rules.Use detailed calculation (based on LCI) for complete LCA.Scenarios for processing of packaging waste should be based on specific national data.

Back to 4.4. Module A5

B- 08. “Repair with complete LCA”

Aspect B- 08. “Repair with complete LCA”
Description
Repair module covers all corrective, responsive or reactive treatment of a construction product or construction works to return it to a condition in which it can perform its required functional and technical performance. It covers only the partial replacements of components and building parts (in case of failure), and shall be distinguished from the replacement module that is related to the complete replacement of component and building parts. This aspect of EEB Guide also addresses the distinction between Repair, Maintenance and Replacements.

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 The reparation procedure refers only to corrective, responsive or reactive actions in response to losses of performances of a building component or building part.Repair is distinguishable from Maintenance and Replacements by the following aspects [EN 15804]:

  • Maintenance is a planed (proactive) action that maintain components performances whereas Repair is a corrective (reactive) action in response to damage;
  • Replacement covers the complete replacement of a component whereas Repair covers only replacement of sub-components.

It should be noted that:

  • EPD containing information about the reference service life of a product shall comply to the ISO 15686 series [EN 15804];
  • RSL shall be declared with a description of use that should (normally) encompass maintenance (proactive actions), according notably to ISO 15868-8;
  • Manufacturer cannot be held responsible for the actual design of the building and the use and application of the product, environment, workmanship or use [EN 15804].

It is thus to be expected that few information related to the repair module will be included in cradle to grave EPDs (or cradle to gate with corresponding options). Instead, most information would probably be divided between the maintenance module (necessary operations to maintain product performances, including sub-component replacement, in a given set of in use conditions) and Replacement module (replacement at the end of life of the component).

Consequently, the Repair module is considered optional in the context of the present guide.

According to EN 15978, the boundary for repair shall include:

  • the production of the repaired part of component and ancillary products;
  • the transportation of the repaired part of component and ancillary products, including production impacts
  • and aspects of any losses of materials during transportation;
  • the repair process of the repaired part of component and ancillary products;
  • waste management of the removed part of the component and of ancillary products;
  • the end of life stage of the removed part of the component and of ancillary products

Water and energy usage related to the repair process should always be included.

Rules from:
EN 15978:7.4.4.1 General7.4.4.4 Boundary for repair (module B3)8.3 Time related characteristics8.6.3 Scenarios for maintenance, repair, replacement

EN 15804:

6.3.3. Reference service life

6.3.4.4.2  – B3 Reparation

7.3.3.1 B1-B5 use stage related to the building fabric

Annex A

Guidance
Repair is optional in the context of complete LCA in the case of insufficient data.The overall repair scenario should be consistent with respect to the building structure (e.g. replacement of coating is mandatory when replacing the support). In the context of complete building LCA of an existing building, it is recommended to base the repair module on the history of the building.The progressive loss of performances of some component has an impact on the overall behavior of the building (e.g. loss of performance of insulation may lead to an increase of energy demand due to heating). If sufficient data are available these aspect should be addressed by using a sensitivity analysis.

Back to 5.4.  Module B3

B- 09. “Repair with simplified LCA”

Aspect B- 09. “Repair with simplified LCA”
Description
Repair module covers all corrective, responsive or reactive treatment of a construction product or construction works to return it to a condition in which it can perform its required functional and technical performance. It covers only the partial replacements of components and building parts (in case of failure), and shall be distinguished from the replacement module that is related to the complete replacement of component and building parts.

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 Repair is optional in the context of simplified LCA. For provision and guidance, please refer to the aspect “Repair with complete LCA” of the present document.The reparation procedure refers only to corrective, responsive or reactive actions in response to losses of performances of a building component or building part.Repair is distinguishable from Maintenance and Replacements by the following aspects [EN 15804]:

  • Maintenance is a planed (proactive) action that maintain components performances whereas Repair is a corrective (reactive) action in response to damage;
  • Replacement covers the complete replacement of a component whereas Repair covers only replacement of sub-components.

According to EN 15978, the boundary for repair shall include:

  • the production of the repaired part of component and ancillary products;
  • the transportation of the repaired part of component and ancillary products, including production impacts
  • and aspects of any losses of materials during transportation;
  • the repair process of the repaired part of component and ancillary products;
  • waste management of the removed part of the component and of ancillary products;
  • the end of life stage of the removed part of the component and of ancillary products

Water and energy usage related to the repair process should always be included.

However, in the context of simplified LCA, only the production of the replaced component/repaired part may be included.

Rules from:
EN 15978:7.4.4.1 General7.4.4.4 Boundary for repair (module B3)8.3 Time related characteristics

8.6.3 Scenarios for maintenance, repair, replacement

EN 15804:

6.3.3. Reference service life

6.3.4.4.2  – B3 Reparation

7.3.3.1 B1-B5 use stage related to the building fabric

Annex A

Guidance
Repair is optional in the context of simplified LCA. For provision and guidance, please refer to the aspect “Repair with complete LCA” of the present document.

Back to 5.4.  Module B3

B- 10. “Repair with screening LCA”

Aspect B- 10. “Repair with screening LCA”
Description
Repair module covers all corrective, responsive or reactive treatment of a construction product or construction works to return it to a condition in which it can perform its required functional and technical performance. It covers only the partial replacements of components and building parts (in case of failure), and should be distinguished from the replacement module that is related to the complete replacement of component and building parts.

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 Repair is optional in the context of screening LCA. For provision and guidance, please refer to the aspect “Repair with complete LCA” of the present document.The reparation procedure refers only to corrective, responsive or reactive actions in response to losses of performances of a building component or building part.Repair is distinguishable from maintenance and replacements by the following aspects [EN 15804]:

  • Maintenance is a planed (proactive) action that maintain components performances whereas Repair is a corrective (reactive) action in response to damage;
  • Replacement covers the complete replacement of a component whereas Repair covers only replacement of sub-components.

According to EN 15978, the boundary for repair should include:

  • the production of the repaired part of component and ancillary products;
  • the transportation of the repaired part of component and ancillary products, including production impacts
  • and aspects of any losses of materials during transportation;
  • the repair process of the repaired part of component and ancillary products;
  • waste management of the removed part of the component and of ancillary products;
  • the end of life stage of the removed part of the component and of ancillary products

However, in the context of screening LCA, only the production of the replaced component/repaired part may be included.

Rules from:
EN 15978:7.4.4.1 General7.4.4.4 Boundary for repair (module B3)8.3 Time related characteristics

8.6.3 Scenarios for maintenance, repair, replacement

EN 15804:

6.3.3. Reference service life

6.3.4.4.2  – B3 Reparation

7.3.3.1 B1-B5 use stage related to the building fabric

Annex A

Guidance
Repair is optional in the context of screening LCA and may be neglected in many cases. For provision and guidance, please refer to the aspect “Repair with complete LCA” of the present document.

Back to 5.4.  Module B3