ISO/DIS 15686-3.2:2025(en)
ISO/TC 59/SC 14
Secretariat: BSI
Date: 2025-09-03
Buildings and civil engineering works— Service life planning — Part 3: Methods, data and communication
Élément introductif — Élément central — Partie 4: Titre de la partie
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Contents Page
Foreword 6
Introduction 7
Part 4: Methods, data and communication 9
1 Scope 9
2 Normative references 9
3 Terms and definitions 9
4 Overview (informative) 11
4.1 Process map 11
4.2 Methods, data and communication 12
5 Common requirements 13
5.1 Objectives 14
5.2 Information 14
5.2.1 Contextual information 14
5.2.2 Input information 14
5.2.3 Data quality 14
5.3 Method 15
5.3.1 Units 15
5.3.2 Grades 15
5.4 Outcomes 15
5.4.1 Output information 15
5.4.2 Presentation 15
6 Product and material identification 16
6.1 Objectives 16
6.2 Information 16
6.2.1 Contextual information 16
6.2.2 Input information 17
6.3 Method 17
6.4 Outcomes 18
6.4.1 Output information 18
6.4.2 Presentation 18
7 Testing and provision of service life metrics 18
7.1 Objectives 18
7.2 Information 19
7.2.1 Contextual information 19
7.2.2 Input information 19
7.3 Method 20
7.3.1 Service-life data from performance in use 20
7.3.2 Service-life data from testing 20
7.4 Outcomes 21
7.4.1 Output information 21
7.4.2 Presentation 21
8 Product estimated service life 22
8.1 Objectives 22
8.2 Information 23
8.2.1 Contextual information 23
8.2.2 Input information 23
8.3 Method 24
8.3.2 Service life by estimation 25
8.3.3 Facility service life 27
8.3.4 Service life data from practical experience 27
8.3.5 Service life for innovative components 27
8.4 Outcomes 28
8.4.1 Output information 28
8.4.2 Presentation 28
9 Appraisal of components in use and their residual service life 28
9.1 Objectives 28
9.2 Information 28
9.2.1 Contextual information 28
9.2.2 Input information 29
9.3 Method 29
9.3.1 Assessing residual service life 29
9.4 Outcomes 29
9.4.1 Output information 29
9.4.2 Presentation 29
10 Uncertainty 29
10.1 Uncertainty and reliability 29
10.1 Representing uncertainty 30
10.1.1 Certain data 30
10.1.2 Simple uncertainty 30
10.1.3 Detailed uncertainty 31
Annex A : Templates and examples 33
A.1 Introduction to templates 33
A.2 References to other sources for templates 33
A.3 Terms used in templates 33
A.4 Overview 33
A.5 Template and example for general considerations 33
A.6 Template and example for product/material/assembly identification, characteristics and quantities (clause 6) 34
A.6 A.7 Template and example for product service life testing (clause 7) 34
A.8 Template and example for design assessment (clause 8) 39
A.9 Template and example for in-use assessment of residual service life (clause 9) 39
A.7 A.10 Sub-Template and example for uncertainty (clause 10) 40
Annex B : Data definitions 41
B.1 B.1 Introduction to data definitions 41
B.2 B.2 References to other sources for data definitions 41
B.3 B.3 Terms used in data definitions 41
B.4 B.4 Overview (clause 4) 41
B.5 B.5 Data definitions for common attributes (clause 5) 41
B.6 B.6 Data definitions for product/material/assembly characteristics and quantities (clause 6) 42
B.7 B.7 Data definitions for product service life testing (clause 7) 42
B.8 B.8 Data definitions for design assessment (clause 8) 43
B.9 B.9 Data definitions for in-use assessment of residual service life (clause 9) 44
B.10 B.10 Data definitions for uncertainty (clause 10) 46
Bibliography 47
Foreword
ISO (the International Organization for Standardization) is a worldwide federation of national standards bodies (ISO member bodies). The work of preparing International Standards is normally carried out through ISO technical committees. Each member body interested in a subject for which a technical committee has been established has the right to be represented on that committee. International organizations, governmental and non-governmental, in liaison with ISO, also take part in the work. ISO collaborates closely with the International Electrotechnical Commission (IEC) on all matters of electrotechnical standardization.
The procedures used to develop this document and those intended for its further maintenance are described in the ISO/IEC Directives, Part 1. In particular, the different approval criteria needed for the different types of ISO document should be noted. This document was drafted in accordance with the editorial rules of the ISO/IEC Directives, Part 2 (see www.iso.org/directives).
ISO draws attention to the possibility that the implementation of this document may involve the use of (a) patent(s). ISO takes no position concerning the evidence, validity or applicability of any claimed patent rights in respect thereof. As of the date of publication of this document, ISO had not received notice of (a) patent(s) which may be required to implement this document. However, implementers are cautioned that this may not represent the latest information, which may be obtained from the patent database available at www.iso.org/patents. ISO shall not be held responsible for identifying any or all such patent rights.
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For an explanation of the voluntary nature of standards, the meaning of ISO specific terms and expressions related to conformity assessment, as well as information about ISO's adherence to the World Trade Organization (WTO) principles in the Technical Barriers to Trade (TBT), see www.iso.org/iso/foreword.html.
This document was prepared by Technical Committee ISO/TC 59, Buildings and civil engineering works, Subcommittee SC 14, Service life planning.
This edition, together with ISO 15686-1:— and ISO 15686-2:—, cancels and replaces ISO 15686-1:2011, ISO 15686-2:2012, ISO 15686-3:2002, ISO 15686-4:2014, ISO 15686-8:2008, ISO/TS 15686-9:2008 and ISO 15686-10:2010, which have been technically revised.
A list of all parts in the ISO 15686 series can be found on the ISO website.
Any feedback or questions on this document should be directed to the user’s national standards body. A complete listing of these bodies can be found at www.iso.org/members.html.
Introduction
The ISO 15686 series on constructed assets, including service life planning, is an essential contribution to the development of a policy for service life planning of constructed assets.
This document specifies methods, data structures and communication activities to be implemented as part of service life planning of constructed assets and their components. Supporting guidance is given in the form of templates and data definitions. The main audience is product, facility and information managers.
For this to occur it is considered that an information system is needed. An information management system suitable for carrying out the service life planning process should, for example, be able to:
— capture enough information and support the methods needed to calculate the effect of the environment and microclimate on the materials and components used,
— define maintenance schedules for different qualities of materials installed under different environmental conditions.
— apply life cycle costing methodologies using the captured data to calculate the benefits of using either high performance materials with little maintenance or lower performance materials with better maintenance procedures. Procedures need to be able to take ease of replacement and demolition into account,
— incorporate new knowledge and predictive methods for material performance and maintenance without affecting methods and data structures that enable calculations based on current knowledge,
— support interoperability between software applications, and
— be used by designers, constructors, owners, operators and demolishers throughout the built asset life cycle.
In practice, this means applying the technology that is generally being termed information management and in some cases building information modelling (BIM) systems. BIM and the use of software applications that enable it is becoming a normal way of working within the built environment sector It offers significant benefits including the ability to work with components and assemblies as objects that encapsulate both shape (in the form of geometric information) and other information about performance, delivery, operation and more. Performance can include information about durability and sustainability metrics. This offers powerful capabilities for dealing with these key areas of interest at every level from individual component to constructed facility.
This document is particularly concerned with the provision of information for service life planning. It proposes structures for the capture and exchange of service life planning information based on the Industry Foundation Classes (IFC) standard for information exchange and sharing.
Clause 4 provides the service life planning context within which it is prepared. Clauses 5 to 10 each covers a stage of the lifecycle of service life information .c, starting with its measurement and publication, followed by its adjustment in the context of a particular facility and finally its use in whole-life calculations. Annexes A and B summarize the standard properties and provide worked examples of how the data might be used in manual or automated calculations.
Buildings and constructed assets — Service life planning — Part 3: Methods, data and communication
1.0 Scope
This document provides requirements and guidance on the methods, data, and communication of service life planning of constructed assets and their components as well as the required supporting data.
This document specifies the structure and representation of service life data. It is focused on key exchange requirements underlying four common transactions.
This document can be used:
a) to achieve and maintain a common understanding within the national and project contexts;
b) to establish the desired outcomes and to define appropriate quality;
c) to identify appropriate management effort and tools;
d) to identify necessary effort and resourcing.
Service life planning involves the application of data about elements within constructed assets to enable their design, predicted or estimated service life to be determined and communicated.
2.0 Normative references
The following documents are referred to in the text in such a way that some or all of their content constitutes requirements of this document. For dated references, only the edition cited applies. For undated references, the latest edition of the referenced document (including any amendments) applies.
ISO 15686‑1, Buildings and constructed assets — Service life planning — Part 1: Concepts and principles
ISO 15686‑2, Buildings and constructed assets — Service life planning — Part 2: Process considerations
ISO 15686‑7, Buildings and constructed assets — Service life planning — Part 7: Performance evaluation for feedback of service life data from practice
ISO 16739‑1, Industry Foundation Classes (IFC) for data sharing in the construction and facility management industries — Part 1: Data schema
ISO 80000, — Quantities and units
3.0 Terms and definitions
For the purposes of this document, the following terms and definitions apply.
ISO and IEC maintain terminology databases for use in standardization at the following addresses:
— ISO Online browsing platform: available at https://www.iso.org/obp
— IEC Electropedia: available at https://www.electropedia.org/
3.1
object
unique occurrence of an item belonging to a class such that the attributes and constraints are defined by the class, having its own identity, behaviour and values for its attributes (state)
3.2
property set
grouping of properties that belong together based on some principle.
EXAMPLE A principle can be life cycle stage or purpose
3.3
quantity set
grouping of characteristic measure properties
4.0 Overview
4.1 Process map
The process map (see Table 1) shows the sequence of processes (ISO 15686-2) and information exchanges (this document) in context.
In summary, this part covers four methods for working with service life data.
— Clause 6: covers the specification/selection of product: product and testing are brought together to obtain the service life characteristics;
— Clause 7: covers the testing regimen and the key service life metrics: the characteristics are brought into a specific context to obtain a predicted service life;
— Clause 8: covers the facility context and the predicted/estimated service life: the predicted or measured service life is used with cost or environmental impact rates to obtain a life cycle cost or assessment;
— Clause 9: covers the impacts (to date and predicted) for stages in the life cycle value: the context factors are revised to reflect in-use surveys.
To support these:
— Clause 5: defines the common requirements for applying this document
— Clause 10 covers the consideration and representation of uncertainty
— Clauses A.6 to A.10 offers templates
— Clauses B.6 to B.10 offer formal data definitions
Table 1 — Service life processes and information requirements
| Testing and inspection | Publication | Prediction | Appraisal |
Manufacturer | ISO15686-3 Clause 6 |
|
|
|
Tester | ISO15686-2 Clause 5 | ISO15686-3 Clause 7 |
|
|
Product data supplier |
| ISO15686-2 Clause 6 | ISO15686-3 Clause 8 |
|
Facility designer or manager | ISO15686-7 | ISO15686-2 Clause 7 | ISO15686-3 Clause 9 | |
Service life consultant |
|
| ISO15686-5 |
The determination of service life is undertaken at various times during the product development and during design, construction and operation of a facility. During the early design stages when product information is aggregated a level such as the whole facility or as specifications of whole systems; it is only the design life of a product that can be determined. At the earliest design stages when only product occurrences are defined, the design life is estimated at the occurrence level. At later design stages, when individual products are located and these products are designated by type, the design life can be indicated for all occurrences at the type level. Similarly, when individual products are identified, it becomes possible to determine a reference service life when a manufacturer/supplier can be identified. As with the design life, the reference service life can be allocated to the product type level.
At later design stages and during construction, when the configuration and location of products has been fully established, it becomes possible to analyse the service life of products according to in-use conditions. These conditions can vary the reference service life depending on factors such as exposure to weather, aggressiveness of the local environment and other degrading (or upgrading) factors. The result of applying in-use conditions is to define an estimated service life which is simply the length of time of a product occurrence life cycle.
Finally, the condition of a product occurrence can be checked from time to time during the operational stage. From the condition of the product, a residual service life can be assessed. If degradation is more than has been expected, the residual service life is reduced.
4.1.1 Methods, data and communication
The overall data requirements for the process are summarized in Figure 1.
Figure 1 — The ‘service life planning view’
5.0 Common requirements
5.1 Objectives
The application of any of the methods detailed in Clauses 6 to 10 shall be based on clear objectives including the desired outcome and the acceptable levels of confidence.
5.1.1 Information
5.1.2 Contextual information
Context information shall be provided, including:
a) identification of the product or facility;
b) identification of the responsible author;
c) identification of the commissioning client;
d) date and version of the report;
e) statement that the study has been conducted in accordance with all the requirements of this document.
5.1.3 Input information
The information inputs shall be clearly stated with their source and confidence.
Sources of data and any third-party assessment or test results shall be provided to enable the data user to assess the quality of the data.
The basis, including the sources and quality of the data used, shall be clearly stated in a written report.
NOTE This is essential to enabling the judgement of the quality of the service-life prediction being undertaken and to enabling risk of error to be adequately considered.
5.1.4 Data quality
The quality of both input data/information and output data/information shall be stated in the report of any service life planning activity.
NOTE The quality of service life estimation depends in part on the quality of the data used to generate the service life estimation. A possible problem with observations in situ is that agents (e.g. weather conditions) can be not reported, or those reported can be not typical, and can not reflect conditions comparable to those to which a component would be exposed in service. Anecdotal evidence of performance is less reliable than scientific evidence, but can be all that is available. In addition, selective reporting of data can be encountered when commercial interests are involved (e.g. a supplier might report positive, but not negative, exposure results). It is to be expected that the situation will improve when criteria are established for the scope and quality of data to be supplied by manufacturers and others for inclusion in databases, and as computer-integrated knowledge systems for service life estimation are developed.
5.2 Method
5.2.1 General
The method applied shall be clearly stated including a reference to Clauses 6 to 10 and any deviations noted.
The report shall also provide the assumptions underlying the estimations.
5.2.2 Units
Values related to the service lives shall be expressed in a period of years, whether they consist of discrete values, such as mean values and standard deviations, or full distributions. For the description of the in-use condition(s), where applicable, the International System of units (SI) shall be used. Symbols for quantities shall be chosen, wherever possible, in accordance with the ISO 80000 series.
5.2.3 Grades
Grades shall be expressed in phrases taken from a verbal scale unless there is a clear numeric metric for intensity available for both reference and contextual situations.
5.3 Outcomes
5.3.1 Output information
The information outputs shall be clearly stated with their confidence.
The report shall also provide a conservative estimate of the uncertainty.
Note: These records can be required for a subsequent review or audit.
5.3.2 Presentation
The context, inputs, method and outputs shall be presented in a structured and clear format.
Results shall be communicated to the parties who can use the information so that they are aware of the actions implied. The results of the study shall be reported to all interested parties.
The findings of all analyses, data, methods, assumptions and limitations shall be presented in sufficient detail to enable assessment the quality of the information. The report shall also allow the results and interpretation to be used in a manner consistent with the goals of the study.
The report shall include measured, calculated or estimated statistical distributions (see Clauses 10 and A.10).
NOTE 1 Distributions can, for example, be expressed in terms of distribution functions, standard deviations or levels of confidence.
NOTE 2 These records can be required for a subsequent review or audit.
NOTE 3 Clauses A.6 to A.10 provide presentation templates.
NOTE 4 Clauses B.6 to B.10 provide formal information specifications.
6.0 Product and material identification
6.1 Objectives
This clause along with clause 5 provides the definition of a product typically by the manufacturer so that the information associated can be exchanged and used, particularly by testing organizations. The identification of a product is central to the effective persistence of the information.
This subclause defines the representation of the characteristic measures of a product as a quantity set. Performance characteristics specific to its specification and selection can also be added. These characteristics are relevant to deeper searching and the construction of benchmarks and comparators.
6.1.1 Information
6.1.2 Contextual information
A detailed description of the product, component, material or assembly shall be provided.
Context information shall be provided, including:
a) the product, initially as an abstract library type and latterly as an instantiated occurrence;
b) the identity of the product, including its name, description and other properties that make it uniquely identified;
c) the source of the product, in terms of the originating organizations, author, and any reference documents;
d) optionally, classification and grouping of the product according to local practice which aids in the searching and the reporting of the product; one or more classifications can be associated to a product:
— name, source and edition of the classification system;
— name and description of the classification entry.
e) component description, comprising:
— main or other identification marks of the components;
— designation of the components in accordance with recommendations or prescriptions expressed in official standards or regulations;
— description of the components;
f) an owner history with a definition of the authoring person and organization; these can have full address and contact details:
— authoring person and organization with role;
— application or method used;
g) additional information relating to constituent components:
|
|
| — model descriptions; |
|
|
| — name and address of manufacturer or supplier of the components; |
|
|
| — date of supply of the components. |
6.1.3 Input information
The component to be evaluated shall be characterized thoroughly in terms of structure, physical properties and chemical composition.
6.2 Method
Methods for determining the quantities and characteristics are out of scope.
NOTE ISO 12006-3 specifies dictionaries suitable for defining such quantities and characteristics.
6.2.1 Outcomes
6.2.2 Output information
General
This subclause defines the representation of the characteristic measures of a product as a quantity set. Performance characteristics specific to its specification and selection can also be added. These characteristics are relevant to deeper searching and the construction of benchmarks and comparators.
Functional measures and quantities
Information shall be provided for characteristic functional measures and quantities. If no measure is given then a unit count shall be assumed. In the case of materials and layered constructions, a unit volume or area shall be provided.
Selection and performance characteristics
Information shall be provided for characteristic selection and performance properties. The selection of these properties may be specific to the type of product, the locale and the procurement method.
7.0 Testing and provision of service life metrics
7.1 Objectives
Clause 7 along with clause 5 covers the testing regimen and the key service life metrics for the publication of product data, typically by testing organisations and product data publishers so as to associate service life information to a generic or specific material or assembly.
This clause adds representation of the testing regime that has evaluated a product and the key service life metrics so as to associate service life information to a generic or specific material or assembly, for use in the subsequent use cases. The authority for the metrics is documented so that the metrics can be verified by recourse to the original source.
7.1.1 Information
7.1.2 Contextual information
Products shall have their several possible applications or intended uses described. intended uses and any limits on in-use conditions for which it is suitable shall be provided. Guidance shall be given on the end uses to which the service-life data provided are relevant.
Context information shall be provided, including:
— identification of the product;
— identification of the responsible author, appointer;
— date and version.
7.1.3 Input information
The information inputs shall be clearly stated with their source and confidence.
The reference service (in-use) conditions and degradation agents to which the component is expected to be exposed in service shall be given. Where the reference (in-use) conditions assume specific provisions for particular measures, these shall be stated. Such measures may include:
— use of a protective coating or cover;
— use of a given (minimum) thickness of material;
— recommendations on installation conditions in the works;
— recommended maintenance requirements.
Reference service life shall be stated as either a single value (e.g. a modal value) or a statistical distribution for the assessment or testing under particular conditions under the prescribed conditions.
The reference in-use conditions, as well as the reference service life, shall be stated so that users of the data can judge the possible differences between the reference in-use conditions and the likely actual in-use conditions in a particular case.
NOTE Common sets of reference in-use conditions can be defined by producers or users of products, in order to facilitate comparison of service-life data for a number of products within the same product family.
7.2 Method
7.2.1 General
The method applied shall be clearly stated.
NOTE Service-life data can be obtained from several sources.
Service-life data shall be based on feedback data in accordance with ISO 15686-7 or data resulting from prediction procedures in accordance with ISO 15686-2.
7.2.2 Service-life data from performance in use
NOTE 1 Wherever possible, performance data that have been obtained from practical experience of actual performance under clearly documented in-use conditions should be used for service-life prediction.
Evidence of performance in use shall be documented to ensure transparency.
NOTE 2 ISO 15686-7 gives further guidance on the use of feedback data from actual performance.
7.2.3 Service-life data from testing methods
Where actual performance data under clearly documented in-use conditions are not available, test data shall be used for service-life prediction. If properly documented test data are already available, they shall be used without further testing. Where further testing is required, it shall be performed in accordance with ISO 15686-2.
There are two categories of testing, direct and indirect.
a. Direct testing: the achievement of a certain level of performance in a test of a particular property shall be recognized as being direct evidence of expected service life (e.g. abrasion, fatigue, closing and impact tests).
b. Indirect (proxy) testing: the measurement of “proxy” characteristics shall be correlated to actual performance and hence service life (e.g. porosity for freeze-thaw resistance and hardness for abrasion resistance).
7.2.4 Service-life data from testing timescales
Tests can be long-term, short-term or a combination of both. They can be carried out using small-scale or full-scale specimens, or a combination of both.
a) Long-term tests can include:
1) field exposure;
2) exposure in experimental facilities.
b) Short-term tests can include:
1) accelerated short-term tests;
2) short-term in-use exposures.
7.2.5 Service-life data from testing types
Tests can be either:
a. natural weathering/aging tests, which either give a direct indication of service life (e.g. corrosion tests) or enable normal performance tests to be carried out after treatment, thus allowing the likely degradation under in-use conditions to be determined, or
b. accelerated weathering/aging tests, in which the normal aging process is speeded up to reduce the duration of the test. Care shall be taken to ensure that degradation mechanisms are accelerated and not significantly altered in such tests.
The methodology used to derive the reference service life shall be reported.
The data sources used and a brief explanation of the reasons for their use shall be provided.
7.3 Outcomes
7.3.1 Output information
Information shall be provided for the service life characteristics:
a) service life type;
b) service life;
c) seven service life factors A - G, except where they are defaulted to 1,0,
7.3.2 Presentation
The context, inputs, method and outputs shall be presented in a structured and clear format.
As short-term exposures typically involve a significant degree of uncertainty, the results shall be considered with care.
A report shall include the following information, wherever applicable:
a) Goal and range definition
b) Exposure programme description, including exposure at pre-tests:
1) general exposure situation, i.e. at outdoor exposure data as latitude, longitude, altitude, distance from coast, special factors like high wind, climate type, etc.;
2) design of the exposure programme, including possible maintenance undertaken for samples, and any accidental deviations thereof;
3) environmental data (including any neighbouring dissimilar components), degradation agent intensities and cycling data;
4) exposure period.
c) Performance evaluation description, including evaluation at pre-tests:
1) methods of measurements or inspections;
2) component data, results of measurements or inspections.
d) Interpretation of data:
1) account for external data sources utilized;
2) specific models or algorithms;
3) results of interpretation;
4) limitations of the interpretation, related to methodology as well as to data;
5) data quality assessment.
e) Critical review:
1) details of reviewers;
2) critical review reports;
3) responses to recommendations.
When the results of the SLP are to be communicated to a third party (i.e. an interested party other than the commissioning client and the commissioned specialist of the study), a third-party report shall be prepared, containing all information indicated above, except what is agreed between the commissioning client and the commissioned specialist to be closed information. This report constitutes a reference document and shall be made available to any third party to whom the communication is made.
8.0 Product estimated service life
8.1 Objectives
Clause 8 along with clause 5 covers the facility context and the predicated estimated service life for reliability and flexibility in use for new facility, typically this is for product data publishers and for design and asset managers. .
This clause adds representation of the context of a product and the predicted service life. The context is provided so that the estimate can be verified. The estimate is provided so that it can be reviewed and used in whole life value assessments.
This clause also adds representation of the economic and environmental impacts of a product, both to-date and ongoing.. Cost is generalized to be an Impact value, thereby ensuring that economic and environmental accounting can be documented. For example, economic cost can be documented along with climate change measures.
Each impact shall be described and the basis of any value shall be given.
NOTE 1 These values can be used to construct aggregate values for aspects of the facility.
8.1.1 Information
8.1.2 Contextual information
Context information shall be provided, including:
a. identification of the instance and its site, facility, system, location
b. identification of the responsible author, appointer
c. date and version
8.1.3 Input information
When developing service life predictions for products or components, a specific or generic set of in-use conditions shall be identified for documenting the specific study. This shall account for the specific use of the component, covering the design consequences, and shall comprise a description of the environment, including static and dynamic mechanical stress, at the site where a buit asset is planned. A description of the effects of occupancy (such as water vapour, heat or abrasion) and the principles on which the built asset is operated (e.g. high or low thermal inertia) shall also be included if appropriate.
Estimated service life shall take account of the aspects that will influence the performance and degradation of the components throughout their service life and will therefore modify the reference service life, including:
a. inherent performance of the component;
b. design level of the works;
c. standard of workmanship;
d. indoor environment;
e. outdoor environment;
f. usage conditions;
g. maintenance level.
Predicted/estimated service life. This uses the same property set as for product reference service life (Clause 6) but with the service life type set to EXPECTED SERVICE LIFE. Context grades for evaluations (matching factors A-G) shall be associated to the product or to the nearest space, storey, facility, site or project in which the product occurs, based on a n-point, typically 5-point, scale.
NOTE The context parameters that are neutral or have no effect on service life can be omitted from this data set.
The product utilization shall be given or a utilization of 1,0 (100 %) shall be assumed if not available.
8.1.4 Input information relating to impacts
Information shall be provided for:
a) Name and description of impact with a value with unit.
b) Life cycle stage, with duration if applicable.
c) Source
NOTE Justification and documentation of service life data used in Environmental Product Declarations are required by EN 15804. These requirements are based on the ISO 15686 series.
8.2 Method
An estimate of the service life of a built aset shall be built up from estimates of the service life of all the relevant components that comprise the built asset. Estimates shall be based on a reference service life.
8.2.1 Similarity of in-use conditions
Data based on reference in-use conditions similar to the object-specific in-use conditions shall be sought to:
— keep the modifying factors as close to unity as possible, thus minimizing the probability of error in the ESL due to uncertainty in the way mechanisms of degradation are taken into account by the modifications;
— minimize the probability that a critical property not encompassed by data becomes the terminal critical property.
NOTE To judge which reference in-use conditions are most similar to, or deviate the least from, the object-specific in-use conditions, consideration can be given only to the in-use conditions or degradation agents known to, or believed to, have the greatest impact on the service life.
8.2.2 Service life by estimation
Factor based estimation shall consider seven discrete aspects given in Table 2.
Table 2 — Factors and factor categories of the factor method
Aspect | Factor | Name | Description |
Inherent quality | A | inherent performance level | the grade of the component as supplied. EXAMPLE Specific durable softwood species, together with timber preservation, jointing and applied coatings for a softwood window lead to a very high inherent performance level. |
| B | design level | the component’s installation in the constructed asset and is typically based on the level of shelter and protection from agents provided by the design of the constructed asset. EXAMPLES An overhanging roof can provide extra protection to the wall below; a reflective coating can prevent cladding exposed to sunlight reaching a critically high temperature. |
| C | work execution level | the level of skill and control in sitework, based on whether the sitework is (or likely to be) in accordance with manufacturers' recommendations and tightly controlled, including issues such as storage, protection during installation, ease of installation, number of trades required for each activity, site applied coatings, etc. |
Environment quality | D | indoor environment | the exposure of the object to indoor agents of degradation and their severity. The general use of the constructed asset is taken into account, together with relevant local aspects (e.g. locations subject to wetting, such as kitchens and bathrooms). |
| E | outdoor environment | the exposure to outdoor agents of degradation and their severity. A meso- or local-level designation can be adequate (e.g. coastal, polluted) for this factor category. However, for detailed design it can be necessary to take into account the microenvironment (e.g. southern elevation, wind suction or uplift at high-level, salt-spray zone). A combination of the agents can have a critical effect (e.g. a combination of wetting and freezing). Observe also that components can be exposed to both external weathering and below-ground water. |
|
|
| NOTE Indoor and outdoor environments are separated and for most components only one such factor category applies; but certain components (e.g. those embedded in the building envelope) can be subject to degradation from both internal and external agents. |
Operational quality | F | usage conditions | the effect of the use of the constructed asset. The specific use of the space where the component is installed or the assembly constructed is likely to be relevant (e.g. communal areas are subject to greater wear and tear). Activities present outside (adjacent to) the constructed asset can also be relevant (e.g. delivery areas subject to mechanical impacts by vehicles). |
| G | maintenance level | the level of maintenance assumed. For certain components that are inaccessible or require special equipment for access, a particularly low maintenance level shall be considered. The expertise of cleaning and the risk of the introduction of agents not normally found (e.g. alkalis) can also be taken into account. |
Rebasing can be applied to convert between types of services life such as from a reference or maximum service life to an estimated life.
L2 = L1 * Π (ϕ2i/ϕ1i)
where:
| L | Service Life (years) |
| Subscript 1, 2 | Input (1) and Output (2) service life type |
|
| (chosen from reference, estimated, maximum, minimum) |
| Subscript i | Factors A-G |
| ϕ | Factor based on grade (where relevant) (see Table 3) |
Table 3 — Factors associated with grade
Grade | ϕ | Description |
Very low | 0,8 | Minimum service life |
Low | 0,9 |
|
Normal | 1,0 | Reference service life |
Good | 1,1 |
|
Very good | 1,25 | Maximum service life |
8.2.3 Facility service life
Lf = min (Lc )
where:
| L | Service Life |
| Subscript f, c | Facility and (non-replaceable) component |
8.2.4 Service life data from practical experience
If available, data from practical performance of components shall be used for service life estimation, as described in ISO 15686-7. Where appropriate, service life data from practice shall be adjusted using the approach specified in 7.3.1 making a judgement of the conditions in which the available data apply and those to which the component will be exposed in service.
8.2.5 Service life for innovative components
NOTE: Innovative products can provide superior performance and overcome long-standing problems.
For the service life estimation of built assets constructed with innovative components, estimates therefore shall be based on interpretation of the performance of the materials and components in short-term exposure tests. In this case, test procedures failure mode and effect analysis (FMEA) and the application of knowledge of material science shall be used to determine a minimum service life for the innovative component.
8.3 Outcomes
8.3.1 Output information
The information outputs shall be clearly stated with their confidence.
The outputs shall include:
a. The estimated service life of systems, product types and/or instances
b. The resultant estimated service life of the facility
8.3.2 Presentation
The context, inputs, method and outputs shall be presented in a structured and clear format.
9.0 Appraisal of components in use and their residual service life
9.1 Objectives
Clause 9 along with clause 5 covers the appraisal of components in use and their residual service life typically for design and asset managers and their consultants
9.1.1 Information
9.1.2 Contextual information
Context information shall be provided. including the
a. identification of the product or facility
b. identification of the responsible author, appointer
c. date and version
9.1.3 Input informationDone.Done.
The information inputs shall be clearly stated with their source and confidence.
9.2 Method
9.2.1 Assessing residual service life
L2 = L1 × ×
×
×
×
×
×
(take into account actual condition, and anticipated change to degradation agents, facility use, etc )
LR = A –LE
Where:
| L | Service Life |
| Subscript R, E | Estimated (E) and Residual (R) service life |
| A | Age (years) |
|
|
|
| ϕ | Factors a-g |
9.3 Outcomes
9.3.1 Output information
The information outputs shall be clearly stated with their confidence.
The outputs shall include:
a. The residual service life of systems, product types or instances
b. The resultant residual service life of the facility
9.3.2 Presentation
The context, inputs, method and outputs shall be presented in a structured and clear format.
10.0 Uncertainty
10.1 Uncertainty and reliability
It shall be decided early in the service life planning how uncertainty in the estimated service life shall be taken into account as the reliability of service life estimation depends on the quality of the data available and the appropriateness of assumptions made. In making service life estimations, the form of the distribution shall be determined if possible; otherwise, it shall be assumed.
NOTE 1 Distributions of various aspects of performance, including service life, can be expected within any group of similar items, including built assets and their components. Due to the number of variables involved and the uncertainties in each, and to the inherent variabilities of built assets, service environments, site workmanship, and future maintenance activities, it is not possible to estimate the service life of a built asset or its components precisely.
Evidence shall be sought regarding reliability of service life estimations based on accelerated exposure tests, by investigating the degree of correlation between in situ performance and laboratory test results.
Defects which cause failures to occur very soon after the occupation of a built asset shall be identified and excluded as these “premature defects” do not necessarily lead to wide-scale failure.
NOTE Generally, a higher degree of uncertainty will be acceptable for maintainable components than for components intended to function without maintenance for the life of the built asset.
10.1.1 Representing uncertainty
10.1.2 General
Where the uncertainty associated to an appraisal or prediction is significant, values shall be transmitted with indication of the extent of the uncertainty. Communication shall use one of three alternative representations for service life and environmental values specified in 10.2.2 to 10.2.4.
10.1.3 Certain data
Where a value is known either because the certainty is high or the value is given, then a single value shall be used (see Table 4).
EXAMPLE The climate change impact of an acoustic ceiling tile component is stated as 5 kg CO2e
Table 4 — Simple value
Value kg CO2e |
5,000 |
10.1.4 Simple uncertainty
Where the specification or testing leaves some uncertainty, a bounded value shall be used.
Uncertainty affecting a value shall be described by the upper bound, lower bound and modal value. This approach is commonly adopted when representing informal opinions or capturing generalized experience. In the absence of further detail, it shall be represented and analysed as a ‘triangular’ distribution (see Table 22 and Figure 2) as a working assumption for detailed calculations. To define a triangular distribution, three values shall be provided:
— the modal value, being the most typical or likely value;
— the lowest typical or likely value;
— the highest typical or likely value.
See Tables 5 and Figure 3.
NOTE The average (mean) value can be different from the modal value.
EXAMPLE The climate change impact of an acoustic ceiling tile component is estimated as ranging between 2 kg and 10 kg, with the mostly likely value being 5 kg. The mean impact can be estimated as the average of these figures, 5,7 kg.
Table 5 — Triangular probability density table
Value | Probability density |
2,000 | 0,000 |
5,000 | 0,250 |
10,000 | 0,000 |
Figure 2 — Triangular probability density graph
10.1.5 Detailed uncertainty
Where there is detailed knowledge of the probable performance, a table distribution of values shall be used.
Where there is sufficient data available, uncertainty affecting a value shall be described using cumulative probability, allowing the representation of any probability distribution, including triangular and normal (Gaussian) distributions. A cumulative probability graph shows the probability of a value (Y-axis) not exceeding a stated value (X-axis) (see Table 6 and Figure 3).
EXAMPLE The climate change impacts of a number of acoustic ceiling tile components have been assessed and summarized (see Table 6 and Figure 4).
Table 6 — Cumulative probability table
Value not exceeding kg CO2e | Cumulative probability % |
2,0 | 0,0 |
3,0 | 7,5 |
4,0 | 22,5 |
5,0 | 47,5 |
6,0 | 67,5 |
7,0 | 82,5 |
8,0 | 92,5 |
9,0 | 97,5 |
10,0 | 100,0 |
Figure 4 — Cumulative probability graph
Templates and examples- Introduction to templates
The following tables provide:
a. A template for documenting each information exchange
b. A worked example (using fictitious and non-representative values)
- References to other sources for templates
See the Bibliography [6] to [11] for other sources for templates
- Terms used in templates
Topic refers to the name or short description. Measure indicates the expected data type
- Overview
Templates and examples are provided to illustrate the methods in clauses 5 to 10.
- General considerations
Table A.5 details properties describing general considerations applicable in clauses A.6 to A.9. See also Clause 6 and Annex B.6
Table A.5 — template and example for general considerations
Topic | Example | Measure |
Author | (organisation) | text |
Appointer | (organisation) | text |
Version | V1.1 | text |
Facility or Product | (name) | text |
Information source(s) | (document or web resource) | text |
Information source quality | very high | grade |
Information output(s) | (document or web resource) | text |
Information output quality | very high | grade |
Compliance(s) | ISO15686 | Boolean |
Method(s) | factor method | text |
- Product/material/assembly identification, characteristics and quantities
Table A.6 details properties describing identification, characteristics and quantities. Measures for quantities and units can vary with product and material type. See Clause 6 and Annex B.6
Table A.6 — template and example for product/material/assembly
Topic | Example | Measure |
Product | (identifier) | text |
Manufacturer | (organisation) | text |
Date | 2025 | datetime |
Description | (description) | text |
Classification | (code): (description) | text |
Other identifiers | (identifier) | text |
Quantity | 20 | number |
Unit | (item, m, m2, m3) | text |
- Template and example for product service life testing (clause 7)
The following provides a template and example for the results of product service life testing as an RSL data record. See also Clause 7 and Annex B.7
a) | General information | |||||||||||||
| 123456789; March, 1989; Nikolaj Tolstoy, Gösta Andersson, Vladimir Kucera and Christer Sjöström. | |||||||||||||
b) | Scope | |||||||||||||
| Data are based on an inventory of external building materials of buildings in Greater Stockholm, Sweden. Material quantities were assessed for different types of buildings, age classes, and areas of different concentrations of air pollution agents. Deterioration levels of roofs, facades and windows were estimated for different materials and surface finishes. The survey method of inspecting a statistical sample has been carefully reviewed. The inventory is a part of Nordic project initiated by a joint governmental body of the Nordic countries with the aim of estimating reductions of corrosion damage as a consequence of reduced SO2 emissions. | |||||||||||||
c) | Material | |||||||||||||
| Site-painted, hot-dipped, zinc-coated sheet steel NOTE This information is needed to identify which type of material/component data is valid. These details facilitate the judgement as to whether data are reasonably applicable to the material/component under study, and make it possible to take care of any differences in material/component by adjusting the factor A of the factor method. Here, the description is not very specific because data are based on a broad survey accepting all types of paint. | |||||||||||||
d) | Methodology | |||||||||||||
| Inspection of constructed assets (feedback from practice) NOTE Together with the information provided below under list item i), Data quality, and list item j), Reliability of data, this entry provides useful information to assess the credibility of the data record. Information relating to how the data have been produced can also be needed to understand the way data are presented | |||||||||||||
e) | Reference in-use conditions | |||||||||||||
| Factor E — Factor category: outdoor environment | |||||||||||||
The outdoor environmental conditions refer to the local scale and are given by the conditions prevailing in Greater Stockholm in the mid-1980s. Service-life data are resolved into two geographical sub-areas, “Inner city” and “Outer areas,” as defined in Table A.67.1. | ||||||||||||||
Table A.7.1 — Reference in-use conditions related to factor E for factor category | ||||||||||||||
|
| Sub-area | SO2 concentration |
|
| |||||||||
|
| Inner city | W 20 µg/m3 |
|
| |||||||||
|
| Outer areas | < 20 µg/m3 |
|
| |||||||||
| NOTE Correlation to concentrations of other degradation agents are likely to apply but are not reported. Factor D — Factor category: indoor environment Not applicable. In-use condition grades for factors A, B, C, F and G are given in Table A.7.2. | |||||||||||||
Table A.7.2 — In-use conditions grades of factors A, B, C, F and G | ||||||||||||||
|
| Factor – factor category | In-use condition grade |
|
| |||||||||
|
| A — inherent performance level | Normal |
|
| |||||||||
|
| B — design level | Normal |
|
| |||||||||
|
| C — work execution level | Normal |
|
| |||||||||
|
| F — usage conditions | Normal |
|
| |||||||||
|
| G — maintenance level | Normal |
|
| |||||||||
|
|
|
|
| ||||||||||
NOTE 1 As the data are based on a survey study of buildings sampled by a random technique, on average the factors are all likely to be characterized as “normal”. In particular, for factor A, the inherent performance level, including the colour of the paint, is not specified. NOTE 2 The reference in-use conditions given here are to be compared with the corresponding in-use conditions of the object under study. If the conditions deviate too much, the user of the data may choose not to use the data record, or otherwise to take the differences in in-use conditions into account by adjusting the corresponding factors of the factor method. Observe that, while being based on such a difference, it is up to the user of the data to calculate or judge the particular size of any adjustment. In this case, the only in-use condition that has been tracked is the outdoor environment in terms of SO2 concentration, the average of other in-use conditions is assumed as normal. | ||||||||||||||
f) | Degradation agents | |||||||||||||
| All of the degradation agents that are expected to be of significance are included. | |||||||||||||
NOTE On one hand, this entry is intended to give allowance to declare any limitation of degradation agents applied in an artificial ageing programme. On the other hand, for data based on natural ageing, degradation agents of importance to the material/component in general, while not being present in the climate type in question, are listed here. For example, salt exposure would be an extremely limited agent in a steel-corrosion study carried out in an area distant from the sea, which in turn would limit the use of data to non-saline conditions. | ||||||||||||||
g) | Critical properties and performance requirements | |||||||||||||
| Critical properties and the corresponding performance requirements expressed in classes of certain standards are given in Table A.7.3. | |||||||||||||
| Table A.7.3 — Performance requirements of critical properties | |||||||||||||
|
| Critical property | Performance requirement | Reference |
| |||||||||
|
| Blistering | > 6F | SIS 18 41 93 |
| |||||||||
|
| Cracking | > 4 | SIS 18 41 95 |
| |||||||||
|
| Chalking | > 4 | SIS 18 41 97 |
| |||||||||
|
| Flaking | > 4 | ASTM D772-47 |
| |||||||||
| These properties are usually the ones that are expected to be critical, except for gloss, when particularly high aesthetic performance is required. NOTE 1 RSL is determined from the failure to meet any of the four performance requirements. NOTE 2 This information is needed to enable the user of data to check if the critical properties and performance requirements of the data record and the case under study correspond. If the critical properties deviate, the use of the data becomes questionable; however, different performance requirements, i.e. levels of required performance, may be maintained by adjusting the service life. | |||||||||||||
h) | Reference service life, RSL | |||||||||||||
| RSL and the corresponding standard deviation, σ, expressed in years, are given in Table A.7.4. | |||||||||||||
Table A.7.4 — RSL and standard deviation | ||||||||||||||
|
| Inner city | Outer areas |
|
| |||||||||
|
| RSL | σ | RSL | σ |
|
| |||||||
|
| 6,3 | 4,1 | 8,0 | 0,6 |
|
| |||||||
| NOTE RSL constitutes the major data and the other entries of an RSL data record represent RSL metadata (data on RSL data). | |||||||||||||
i) | Data quality | |||||||||||||
| Data are generated on the basis of a systematic procedure but are not critically reviewed by a third party NOTE The purpose of this entry is to facilitate a rough estimation of the data quality. If a more detailed estimation is desired, the user shall be referred to original documents listed in References [10] to [15]. | |||||||||||||
j) | Reliability of data | |||||||||||||
| Data are provided by non-reviewed, public research documentation NOTE The purpose of this entry is to facilitate a rough estimation of data reliability. If a more detailed estimation is desired, the user shall be referred to original documents listed in References [10] to [15]. | |||||||||||||
k) | Further information considered | |||||||||||||
| Data obtained from the inventory according to list item b) were further processed by Tolstoy [11] from which document RSLs referenced here were retrieved. | |||||||||||||
NOTE See References [10] to [15] to enable the user of data to go back to original documents for any detailed information not included in an RSL data record. References are also a part of quality control. |
- Design assessment
Table A.8 provides a template and example for design assessment. See also Clause 8 and Annex B.8
Table A.8 — Design assessment
Step | Value | Measure |
It is used in a context a where the external environmental grade | LOW (second lowest) | grade |
The utilization ratio assumed for the product | 12,500 | % |
Choosing from a five-point scale | (−1,000, −0,500, 0,000, +0,500, +1,000) | |
The second lowest value is | −0,500 | ratio |
The estimated service life environmental factor | 1,000 + (1,000 − 0,900) × (−0,500)] = 0,950 | ratio |
The estimated service life | 0,950 × 20,000 = 22,800 | years |
The actual utilization ratio (from the occurrence object or facility) | 15,000 | % |
The expected elapsed service life | 22,800 × 0,125/0,150 = 19,000 | years |
a Other factors are taken as normal. |
- In-use assessment of residual service life
Table A.9 provides a template and example for in-use assessment of residual service life. See also Clause 9 and Annex B.9
Table A.9 — template and example for in-use assessment of residual service life.
Step | Value | Measure |
The product(s) is are maintained starting one year after installation Lead In | 1,000 | years |
Maintenance is spread over 2 years Duration | 2,000 | years |
The maintenance cycle restarts 3 years thereafter Lead Out | 3,000 | years |
The number of times in its service life that it will be maintained | 19,000/(1,000 + 2,000 + 3,000) rounded down = 3,000 | number |
Maintenance incurs a carbon equivalent impact of, for example, | 6,000 | kg CO2e |
Impact from maintenance | 6,000 × 3,000 = 18,000 | kg CO2e |
Annualized impact | 18,00/19,00 = 0,950 | kg CO2e per year |
- Uncertainty
Table A.10 provides a sub-template and example presenting uncertainty. See also Clause 10 and Annex B.10 .
Table A.10 — Presentation of uncertainty
Step | Value | Measure |
Maintenance event incurs a carbon equivalent impact | 6,000 | kg CO2e |
Impact value has a lower bound | 4,500 | kg CO2e |
Impact value has an upper bound | 9,000 | kg CO2e |
Maintenance event occurrences | 3,000 | number |
Maintenance incurs a carbon equivalent impact over the service life | (4,500, 6,000, 9,000) × 3,000 = (13,500, 18,000, 27,000) | kg CO2e |
Most likely impact | 18,000 | kg CO2e |
Range of impacts | 13,500 up to 27,000 | kg CO2e |
Data definitions- Introduction to data definitions
IFC contains support for a wide range of built asset topics. The information needed for service life planning and related topics is supported by specific objects (entity types) in the schema (e.g. an object handling functional measures'), but also as general objects handling the technical performance of components and systems, property information (e.g. material) about the components, information about needed measures of care and maintenance etc.
- References to other sources for data definitions
Data definitions can be found at bsDD[20].
- Use of terms in data definitions
Service life factors: Can be applied to any physical object either as a single occurrence or an aggregation or assembly of physical objects acting as a single object. A service life can have one or more related service life factors according to the ISO 15686 factor method. See 7.4.1.
Grade: The current condition of physical objects can be determined by applying one or more condition criteria. The condition can be determined using either subjective assessment (e.g. condition on a graded scale from 1 to 5 where 1 is very poor and 5 is very good or as new) or by objective assessment using measured values. See 8.3.2.
- Overview
There are several concepts captured in the IFC schema that are relevant to service life planning and that can be applied in a specific subset (view) of the IFC schema about service life planning.. See Tables B.5 to B.10.
- Common attributes
Table B.5 provides IFC data definitions for common attributes. See also Clause 5.
Table B.5 — data definitions for common attributes
Topic | Example | Measure |
Author | IfcOrganization | entity |
Appointer | IfcOrganization | entity |
Version | IfcOwnerHistory.ModifiedDate | datetime |
Facility or Product | IfcObject.Name | text |
Information source(s) | IfcDocumentInformation | entity |
Information source quality | IfcDocumentInformation. IntendedUse | grade |
Information output(s) | IfcDocumentInformation | entity |
Information output quality | IfcDocumentInformation. IntendedUse | grade |
Compliance(s) | IfcApproval | entity |
Method(s) | IfcTaskType | entity |
- Product/material/assembly characteristics and quantities
Table B.6 provides IFC data definitions for product/material/assembly characteristics and quantities. See also Clause 6. The data definition for Quantity can vary with different products, materials and assemblies.
Table B.6 — IFC data definitions for product/material/assembly characteristics and quantities
Topic | IFC | Measure |
Product | Pset_ManufacturerTypeInformation. ModelReference | text |
Manufacturer | Pset_ManufacturerTypeInformation. Manufacturer | text |
YearDate | Pset_ManufacturerTypeInformation. ProductionYear | text |
Description | Pset_ManufacturerTypeInformation. ModelLabel |
|
Classification | IfcClassificationReference |
|
Quantity | IfcQuantityCount/Length/Area/Volume/Mass | (varies) |
- Product service life testing
Table B.7 provides IFC data definitions for product service life testing. See also Clause 7.
Table B.7 — IFC data definitions for product service life testing.
Name | Measure | Definition |
---|---|---|
Service Life Type | ACTUAL SERVICE LIFE EXPECTED SERVICE LIFE OPTIMISTIC REFERENCE PESSIMISTIC REFERENCE REFERENCE SERVICE LIFE RESIDUAL SERVICE LIFE | The service life that a constructed asset has given. The service life that an artefact is expected to have under current operating conditions. The best or most optimistic estimate of service life that is quoted for an artefact under reference operating conditions. The least or most pessimistic estimate of service life that is quoted for an artefact under reference operating conditions. The typical service life that is quoted for an artefact under reference operating conditions. The residual service life estimated as remaining, taking into account the operating conditions experienced to date |
Service Life Duration | Duration | The length or duration of a service life. |
Quality Of Components | Positive ratio | Adjustment of the service life resulting from the effect of the quality of components used. Factor A |
Design Level | Positive ratio | Adjustment of the service life resulting from the effect of design level employed. Factor B |
Work Execution Level | Positive ratio | Adjustment of the service life resulting from the effect of the quality of work executed. Factor C |
Indoor environment | Positive ratio | Adjustment of the service life resulting from the effect of the indoor environment (where appropriate). Factor D |
Outdoor Environment | Positive ratio | Adjustment of the service life resulting from the effect of the outdoor environment (where appropriate). Factor E |
In Use Conditions | Positive ratio | Adjustment of the service life resulting from the effect of the conditions in which components are operating. Factor F |
Maintenance Level | Positive ratio | Adjustment of the service life resulting from the effect of the level or degree of maintenance applied to components. Factor G |
- Design assessment
A product instance or its owning space, storey, facility site or project can have service life context grades (Grade A-G)) associated with it. In each of the seven cases, ’grade’ is appended to the factor name. Each grade can be represented using a five-point verbal scale, or it can be ‘not defined’. Table B.8 provides data definitions for design assessment. See also Clause 8.
Table 2 — IFC Data definitions for design assessment
Name | Measure | Definition |
Quality Of Components Grade | — Very high — High — Normal — Low — Very low — Not defined | Grade for adjustment of the service life resulting from the effect of the quality of components used. Grade A |
Design Level Grade | Grade for adjustment of the service life resulting from the effect of design level employed. Grade B | |
Work Execution Level Grade | Grade for adjustment of the service life resulting from the effect of the quality of work executed. Grade C | |
Indoor Environment Grade | Grade for adjustment of the service life resulting from the effect of the indoor environment (where appropriate). Grade D | |
Outdoor environment grade | Grade for adjustment of the service life resulting from the effect of the outdoor environment (where appropriate). Grade E | |
In use conditions grade | Grade for adjustment of the service life resulting from the effect of the conditions in which components are operating. Grade F | |
Maintenance level grade | Grade for adjustment of the service life resulting from the effect of the level or degree of maintenance applied to components. Grade G |
- In-use assessment of residual service life
Table B.9 provides data definitions for in-use assessment of residual service life. See also Clause 9.
Table B.9 — IFC data definitions for in-use assessment of residual service life
Name | Measure | Definition |
---|---|---|
Life Cycle Phase | — Production — Transportation — Installation — Usage — Maintenance — Disposal — Whole life cycle — User defined — Not defined | The whole life cycle or only a given phase from which environmental data are valid |
Activity | Text | Description of included activity |
Duration | Duration measure | Duration of activity considered |
Lead In Time | Duration measure | Time before activity commences |
Lead Out Time | Duration measure | Time after activity completes |
Total Primary Energy Consumption | Energy | Quantity of energy used as defined in ISO 21930 |
Water Consumption | Volume | Quantity of water used |
Hazardous Waste | Mass | Quantity of hazardous waste |
Non-Hazardous Waste | Mass | Quantity of non-hazardous waste generated |
Climate Change | Mass | Quantity of greenhouse gases emitted calculated in equivalent CO2 |
Atmospheric Acidification | Mass | Quantity of gases responsible for the atmospheric acidification calculated in equivalent SO2 |
Renewable Energy Consumption | Energy | Quantity of renewable energy used as defined in ISO 21930 |
Non-Renewable Energy Consumption | Energy | Quantity of non-renewable energy used as defined in ISO 21930 |
Resource Depletion | Mass | Quantity of resources used calculated in equivalent antimony |
Inert Waste | Mass | Quantity of inert waste generated |
Radioactive Waste | Mass | Quantity of radioactive waste generated |
Stratospheric Ozone Layer Destruction | Mass | Quantity of gases destructing the stratospheric ozone layer calculated in equivalent CFC-R11 |
Photochemical Ozone Formation | Mass | Quantity of gases creating the photochemical ozone calculated in equivalent ethylene |
Eutrophication | Mass | Quantity of eutrophicating compounds calculated in equivalent PO4. |
NOTE 1 EN 15804 has recommendations for extensions for the list of life cycle phases. NOTE 2 The property set can be developed further by reference to EN 15942. |
- Uncertainty
Table B.10 provides guidance on data definitions for uncertainty. See also Clause 10.
Table B.10 — IFC data definitions for uncertainty.
Topic | IFC | Measure |
Certain value | IfcPropertySingleValue | (various) |
Range value | IfcPropertyBoundedValue | (various) |
Value distribution | IfcPropertyTableValue | (various) |
Bibliography
[1] ISO 6241, Performance standards in building — Principles for their preparation and factors to be considered
[2] ISO 10303‑11, Industrial automation systems and integration — Product data representation and exchange — Part 11: Description methods: The EXPRESS language reference manual
[3] ISO 10303‑21, Industrial automation systems and integration — Product data representation and exchange — Part 21: Implementation methods: Clear text encoding of the exchange structure
[4] ISO 10303‑28, Industrial automation systems and integration — Product data representation and exchange — Part 28: Implementation methods: XML representations of EXPRESS schemas and data, using XML schemas
[5] ISO 12006‑3, Building construction — Organization of information about construction works — Part 3: Framework for object-oriented information
[6] ISO 14020, Environmental statements and programmes for products — Principles and general requirements
[7] ISO 14021, Environmental labels and declarations — Self-declared environmental claims (Type II environmental labelling)
[8] ISO 14024, Environmental labels and declarations — Type I environmental labelling — Principles and procedures
[9] ISO 14025, Environmental labels and declarations — Type III environmental declarations — Principles and procedures
[10] ISO 14040, Environmental management — Life cycle assessment — Principles and framework
[11] ISO 14044, Environmental management — Life cycle assessment — Requirements and guidelines
[12] ISO 21929‑1, Sustainability in building construction — Sustainability indicators — Part 1: Framework for the development of indicators and a core set of indicators for buildings
[13] ISO 21930, Sustainability in buildings and civil engineering works — Core rules for environmental product declarations of construction products and services
[14] ISO 21931‑1, Sustainability in buildings and civil engineering works — Framework for methods of assessment of the environmental, social and economic performance of construction works as a basis for sustainability assessment — Part 1: Buildings
[15] ISO 29481‑1, Building information modelling — Information delivery manual — Part 1: Methodology and format
[16] EN 15804, Sustainability of construction works — Environmental product declarations — Core rules for the product category of construction products
[17] EN 15942, Sustainability of construction works — Environmental product declarations — Communication format business-to-business
[18] The official website of buildingSMART International is http://www.buildingsmart.com
[19] Most regional buildingSMART groups maintain their own websites accessible from the international site
[20] The buildingSMART Data Dictionary (bsDD) can be accessed at https://www.buildingsmart.org/users/services/buildingsmart-data-dictionary/