PRODUCT-CATEGORY RULES (PCR)

Transcription

1 PRODUCT-CATEGORY RULES (PCR) For preparing an environmental declaration (EPD) for Product Group Solid wood products NPCR 015 September 2009

2 2 Content 1 GENERAL INFORMATION SCOPE TERMS AND DEFINITIONS DECLARED UNIT FUNCTIONAL UNIT INFORMATION MODULE LIFE CYCLE ASSESSMENT (LCA) PLANED TIMBER PRODUCT CATEGORY TYPE III ENVIRONMENTAL DECLARATION, ENVIRONMENTAL PRODUCT DECLARATION, EPD ROUND TIMBER SAWN DRIED TIMBER SOLID WOOD COMPANY/ORGANIZATION, PRODUCT AND PRODUCT GROUP DESCRIPTION OF COMPANY/ORGANIZATION DESCRIPTION OF PRODUCT DEFINITION OF PRODUCT GROUP GOAL AND SCOPE FOR THE UNDERLYING LCA FUNCTIONAL AND DECLARED UNIT SYSTEM BOUNDARIES DESCRIPTION OF DATA CUT-OFF RULES DATA QUALITY REQUIREMENTS UNITS INVENTORY ANALYSIS DATA COLLECTION CALCULATION RULES ALLOCATION RULES COMBUSTION OF WOOD FUELS IMPACT CATEGORIES AND CHARACTERIZATION FACTORS CHARACTERIZATION FACTORS PARAMETERS TO BE REPORTED ADDITIONAL ENVIRONMENTAL INFORMATION ORIGIN OF ROUND TIMBER CHEMICALS OTHER ADDITIONAL ENVIRONMENTAL INFORMATION CONTENT OF THE ENVIRONMENTAL DECLARATION (EPD) GENERAL INFORMATION TO BE DECLARED PERIOD OF VALIDITY OF THE DOCUMENT REFERENCES APPENDIX 1 PROJECT DOCUMENTATION/REPORT APPENDIX 2 HEALTH AND ENVIRONMENTAL RISK IMPACT FROM CHEMICALS APPENDIX 3 INDOOR ENVIRONMENT IMPACT APPENDIX 4 STANDARDS OF RELEVANCE FOR SOLID WOOD PRODUCTS... 22

3 3 GENERAL INFORMATION These product category rules (PCR) are intended for companies preparing an Environmental Product Declaration (EPD) for solid wood products (see chapter 3.3 for definition of product group). The PCR comply with the requirements of the following ISO standards: ISO 21930: 2007, Building construction - Sustainability in building construction Environmental declaration of building products [1], ISO 14025: 2006, Environmental labelling and declarations Type III environmental declarations Principles and procedures [2], ISO 14044: 2006, Environmental management Life cycle assessment Requirements and guidelines [3]. The PCR are based on Life Cycle Assessment (LCA) studies of wood products carried out in the project Nordic Wood (1999) where 43 Nordic companies, mainly sawmills, participated and in the project MIKADO ( ) where 20 companies are participating. The EPD will present data that has been aggregated over the life cycle stages Product stage, Construction stage, Use stage and End of life stage or relevant parts of it. Any EPD following these PCR may also be based on information modules that only cover some only partially cover the stages of the product s life cycle. Program operator: Næringslivets Stiftelse for Miljødeklarasjoner NHO, Postboks 5250 Majorstuen, 0303 Oslo The PCR have been prepared by the members of the PCR Work Group (WG) and SINTEF Byggforsk. Members of the PCR WG: Ole Helge Aalstad Oskar Aarnes Helge Hollerud Anders Nyrud Per Skreden Per Otto Flæte Consultants: Kjersti Folvik Catherine Grini Moelven Mjøsbruket AS (manufacturer) Gausdal Bruvoll BA (manufacturer) Romerike Trelast AS (manufacturer) Norwegian Institute of Wood Technology (Research institute) The Norwegian Sawmill Industries Association Norwegian Forest and Landscape Institute (Research institute) SINTEF Byggforsk SINTEF Byggforsk 1 Scope The intended application of these Product Category Rules (PCR) is to give guidelines for carrying out Environmental Product Declarations (EPD) for solid wood products and to pinpoint the underlying requirements of the LCA. The users of these PCR will be manufacturers of solid

4 4 wood products and other interested parties. These PCR are valid for solid wood products (see chapter 3.3 for definition of product group). 2 Terms and definitions For the purposes of this document, the following terms and definitions apply. 2.1 Declared unit quantity of a building product for use as a reference unit in an EPD (2.7), based on LCA (2.4), for the expression of environmental information needed in information modules (2.3) Example: Mass (kg), Volume (m³) NOTE The declared unit will only be used where the function and the reference scenario for the whole life cycle, on the building level, can not be stated [ISO 21930: 2007] 2.2 Functional unit quantified performance of a product system for a building product for use as a reference unit in an EPD (2.7) based on LCA (2.4) [ISO 21930: 2007] 2.3 Information module compilation of data to be used as a basis for a Type III environmental declaration (2.7), covering a unit process or a combination of unit processes that are part of the life cycle of a product [ISO 21930: 2007] 2.4 Life cycle assessment (LCA) compilation and evaluation of the inputs, outputs and the potential environmental impacts of a product system throughout its life cycle [ISO 14040: 2006] 2.5 Planed timber Sawn timber that, after drying to the end-use moisture content has been machined further in thickness and/or width within tight specified permitted deviations. (EN 844-3:1995) German: gehobeltes Holz French: bois raboté Norwegian: høvellast 2.6 Product category group of building products that can fulfill equivalent functions [ISO 21930: 2007]

5 5 2.7 Type III environmental declaration, Environmental product declaration, EPD environmental declaration providing quantified environmental data using predetermined parameters and, where relevant, additional environmental information [ISO 21930: 2007] 2.8 Round timber Felled tree cross-cut at the top, with all branches removed, that may or may not have been further cross-cut, generally excluding firewood. (EN 844-2:1997) Also called logs, roundwood German: Rundholz French: bois rond Norwegian: tømmer / rundvirke 2.9 Sawn dried timber Timber section produced by the lengthwise sawing or chipping of logs or solid wood of larger dimensions and possible crosscutting and/or further machining to obtain a certain accuracy that has been dried to the end-use moisture content. Norwegian: skurlast 2.10 Solid wood wood, sawn or otherwise machined wood which may include finger jointed and/or laminated wood (EN 335-2:2006)

6 6 3 Company/organization, product and product group 3.1 Description of company/organization The name of the company/organization as well as the place(s) of production shall be provided. General information about the company/organization can be included in the EPD i.e. the existence of quality systems or environmental management system according to ISO or EMAS or any other environmental management system in place [5], [6]. 3.2 Description of product The description of the product shall enable the user to identify the product unambiguously. The characterisation includes: Product identification by name (including e.g. production code) and a simple visual representation of the building product for which the EPD is developed Main technical data and properties of the building product according to the standards listed in Appendix 4 Flow diagram of main production processes according to the scope of the declaration Materials and substances to be declared: Material contents of the finished product, including packaging shall be declared in terms of the main components. Substances officially classified as hazardous according to national and international regulations by CAS-No (EU directive 67/548/EWG) shall be stated. Product specific data that is confidential, because of competitive business environment, intellectual property rights or similar legal restrictions need not to be declared to the public. New requirements concerning declaration of chemicals (REACH directive) shall apply. 3.3 Definition of product group Product group Solid wood products consists of the products described in table 1, in accordance with the terminology given in the standards EN 844-1, EN and EN Table 1: Products covered by these PCR Solid wood product Description / Example of products Sawn dried timber Planed structural timber Planed interior wood products Planed exterior wood products Structural gluelam Sawn dried timber Scantlings, batten, batten trim, beams, joists, studs, finger jointed timber, solid wood elements (without glue) etc. Solid wood panels, internal wood mouldings, wood flooring etc. Cladding, subcladding, with or without industrial coating Decking boards, window sills, railings Solid wood elements Glued laminated timber

7 7 4 Goal and scope for the underlying LCA 4.1 Functional and declared unit These PCR are valid for all solid wood products which are manufactured or processed for incorporation in a building or other construction work. (i.e. building materials, products, components, or building elements). The functional unit or declared unit of a product provides the quantitative normalisation for comparing products of equivalent function. For declarations covering the complete life cycle a functional unit is defined. For declarations not covering the complete life cycle, e.g. leaving out the use stage and/or the end of life stage, a declared unit is defined. If the EPD is intended to be used for comparison of building products, the use stage must be included. Information provided using a declared unit shall not be used in that case. Table 2: Products covered by these PCR with commonly used unit Solid wood product Description / Example of products Unit to be used in EPD Sawn dried timber Sawn dried timber Declared unit (cradle to gate) 1 m³ of sawn dried timber Planed structural timber Scantlings, batten, batten trim, beams, joists, studs, finger jointed timber, solid wood elements (without glue) etc. Planed interior wood products Planed exterior wood products Structural gluelam used in buildings Glued laminated timber used in bridges Solid wood panels, internal wood mouldings, wood flooring etc. Cladding, subcladding, with or without industrial coating Decking boards, window cills, railings Solid wood elements, glued laminated timber Glued laminated timber Functional unit 1 m of installed planed structural timber with an expected average service life of 60 years Functional unit 1 m² of installed planed interior wood product with an expected average service life of 30 years Functional unit 1 m² of installed planed exterior wood product with an expected average service life of 50 years Functional unit 1 m of installed planed exterior wood product with an expected average service life of 50 years Functional unit 1 m³ of installed structural gluelam with an expected average service life of 60 years Functional unit 1 m³ of installed glued laminated timber with an expected average service life of 100 years Other units can be used if expedient. Conversion factor to the unit shown in table 2 shall then be provided.

8 8 4.2 System boundaries The life cycle stages for installed solid wood products are shown in figure 1. Cut-off System boundaries Transport Cradle to gate Cradle to grave Sawn dried timber Transport Energy Production of solid wood products except sawn dried timber Building site Use and maintenance of the product in the building Dismantling/ Demolition Waste collection and sorting Next system Raw materials (<2%mass) Stockist Wood fuel Product stage Allocated to other product systems Packaging included Resources Manufacturing Building site Construction stage Use stage End of life stage Use/Maintenance By-products (reuse / recycling / energy production) Demolition Disposal/Recycling Allocation to next system for material use or energy production Figure 1: System boundaries and life cycle stages of solid wood products (except sawn dried timber). The system boundaries encompass the following processes: Product stage extraction of raw materials transport of raw materials (included recycled materials) from extraction site to production site production of wood product packaging transport from production site to recycling/reuse/land fill (waste and by-products from production) recycling/reuse/energy recovery (waste and by-products from production) Construction stage transport of building products from production site to stockist or directly to building site transport of building products from stockist to building site installation on the building site loss on the building site

9 Use stage The use stage is treated as scenario: the reference service life of the building is defined as 60 years and the number of replacements of the wood products shall be declared accordingly. maintenance of the wood products that will be necessary to get the expected reference service life [7]. Maintenance/replacements are to be modelled according to manufacturers guidelines End of life stage The end of life stage is treated as scenario: dismantling/demolition transport from building site to recycling/reuse/land fill recycling/reuse/energy recovery The production and the installation processes (product and construction stages) shall be declared separately from both the operation/maintenance processes (use stage) and from the demolition processes (end of life stage). The use stage and the end of life stage are both based on typical scenarios for the products. The scenarios shall be described in detail. Any transportation data other than identified above shall be indicated. If transportation information is included in other stages than indicated, or if no transportation information exists and assumptions are made, this should be noted. 4.3 Description of data The use of specific or generic background data shall be documented. As a rule the following distribution will be applied: Production of raw materials (specific and/or average background) Manufacturing of the product (specific) The mix of electricity used should be the official one in the country where main energy consuming processes take place, if site-specific data cannot be obtained. (e.g. Norwegian mix for production sites located in Norway). The mix of electricity (calculation procedure) shall be documented. Hazardous waste shall be specified according to EU Directives 91/689/EEC and 75/442/EEC (specific and/or average background)

10 10 The following source, Table 3, for generic data might be used for the European market. Table 3 Database (example) Material Steel Copper Electricity Aluminium Plastics Chemicals Database IISI (International Iron and Steel Institute) ICA (International Copper Association) ECO-PROFILES of the European plastics industry Methodology Plastics Europe (Association of Plastics Manufacturers) EAA (European Aluminium Association) Plastics Europe (Association of Plastics Manufacturers Europe) Plastics Europe (Association of Plastics Manufacturers Europe) All data have to be specified, including database and year of publication (reference). Sources of data for transport models (including transport form, distances and quantities to be transported) and thermal energy production shall be documented. 4.4 Cut-off rules Any processes or activities that altogether do not contribute to more than 2 % of the total mass and 1 % of the total energy use may be omitted from the inventory analysis. However, omissions of any material flow that may have a relevant contribution to the selected impact categories of the products underlying the EPD shall be justified, if applicable by a sensitivity analysis. A list of hazardous and toxic materials and substances shall be included in the inventory and the cut-off rules do not apply to such substances. 4.5 Data Quality requirements Transport Allocation related to transport shall be based on the weight [tonne km] of transported product. 4.6 Units The following units shall be used: SI units Preferred power and energy units: o kw (MW) for power o kwh (MJ) for electric energy

11 11 5 Inventory analysis 5.1 Data collection The data shall be representative according to temporal, geographical and technological requirements. Temporal: The obtained information from the manufacturing process should be annual approximate values and updated, i.e. from the previous 12-month period. Average background data should not be older than 10 years. Geographical: The geographic region of the production sites included in the calculation of representative data shall be documented. Technological: Data should represent technology in use. 5.2 Calculation rules The amount of material used as input of wood products (functional unit) shall include related accessories and auxiliary materials (screws, prefabricated mountings). Omission of accessories and auxiliary materials shall be justified. 5.3 Allocation rules General allocation rules In a production process where more than one type of product is generated, it is necessary to allocate the environmental impacts (inputs and outputs) from the process to the different products in order to get product-based inventory data. In principle allocation rules should reflect the goal of the production process. Raw material energy shall be allocated to material resources (kg), while process energy shall be allocated to energy resources (MJ). When the product s original function is lost, it can be processed further in a waste management system, e.g. it can be recycled, reused or energy recovered. Restrictions on land filling of organic wastes make production of heat or electricity the most suitable option for wood wastes. The emissions from down stream combustion will be allocated to the new downstream products, i.e. heat and electricity, according to the allocation procedure for open loop recycling. In the case of incineration of wood residues or wastes for energy production at production site, the emissions from the combustion shall, however, be allocated to the product. Recycling processes shall be treated as closed loop recycling, as long as no change occurs in the inherent properties of the recycled material. In such cases, the need for allocation is avoided since the use of secondary material displaces the use of virgin (primary) materials. Recycled materials that are used in the fabrication of the product shall have no environmental impact on the new product. When allocation is used, the economic reality and other relevant aspects shall be considered to determine if other allocation criteria would be more appropriate or lead to deviating results. A

12 12 sensitivity analysis should be initiated if a deviation of > 20% is foreseen. Different data sets shall be documented and reported, if different allocation options are relevant Allocation rules for production at saw mills System boundaries for production of sawn dried timber, pulp chips and sawdust at saw mills are shown in figure 2. Figure 2: System boundaries for production at saw mills For production at saw mills, the allocation shall be carried out according to volume. Impacts from forestry should be allocated to sawn dried timber, pulp chips, sawdust and bark according to volume. Irrigation water should be allocated according to sawn dried timber, pulp chips, sawdust and bark according to volume. Energy use from sawing and drying should be allocated to sawn dried timber exclusively. Energy use related to the utilisation of office and administration premises should be allocated to sawn dried timber, pulp chips and sawdust according to volume. Internal transport should be allocated to sawn dried timber exclusively. Energy and resources use allocated to sawn dried timber at the end of the production process at saw mills are identical with those allocated to shavings (shavings are part of sawn dried timber and will be taken out in the next system).

13 Allocation rules for production of solid wood products (except sawn dried timber) For production of solid wood products, the allocation shall be carried out according to volume and process steps as follow: Energy use required by the operation of the different process equipments should be allocated to solid wood products (including shavings). If the production site produces different types of solid wood products, the energy use of each production chain should be allocated to its respective product. If unknown, the sharing out of the energy use can be done according to the installed power effect and the running time of the equipment required by each solid wood product. Energy use related to the utilisation of office and administration premises should be allocated to solid wood products (including shavings) according to volume. Internal transport should be allocated to solid wood products (including shavings) according to volume. 5.4 Combustion of wood fuels CO 2 emissions due to the combustion of wood fuels are considered equal to the CO 2 uptake in the forestry growth process (neutral CO 2 balance [11]). For this reason, the inventory which the EPD is based on will not include emissions/uptake of CO 2 in relation to wood fuels. To calculate the energy demand covered by by-products on the production site, the gross calorific values given in Table 5 shall be used [12]. Table 4: Gross calorific value and translation factor from loose to solid volume for by-products from saw mills and solid wood industry Type of wood fuel Gross calorific value [MJ/lm³] 1 Translation [fm³/lm³] 2 Green bark ,35 Chips (from root reduction) ,35 Raw pulp chips ,36 Dried pulp chips ,36 Raw sawdust ,33 Dried sawdust ,33 Shavings ,20 1 The unit called lm³ refers to loose volume (loose m³) 2 The unit called fm³ refers to solid volume (fixed m³)

14 14 6 Impact categories and characterization factors 6.1 Characterization factors The factors employed to calculate the selected environmental impacts shall be taken from Table 5. Table 5: Characterization factors Impact category Unit /declared unit Source Global warming potential (GWP) [kg CO 2 equiv] Latest version of IPCC Ozone layer depletion potential (ODP) [kg R11 equiv] CML 2001 Acidification potential (AP) [kg SO 2 equiv] CML 2001 Eutrophication potential (EP) [kg PO 4 equiv] CML 2001 Photochemical ozone creation potential (POCP) [kg C2H4 equiv] CML Parameters to be reported The use of resources and energy should be declared as: Depletion of non-renewable material resources other than primary energy Use of renewable material resources other than primary energy Use of renewable energy resources, primary energy spilt into hydropower, wind power, solar power and biomass Use of non-renewable energy resources, primary energy spilt into use of coal, lignite, natural gas, uranium, secondary fuels Environmental impact should be declared as: Climate change. Emission of greenhouse gases (expressed as the sum of global warming potential, GWP in kg CO2 - equivalents, 100 years). Destruction/depletion of stratospheric ozone layer. Emission of ozone-depleting gases (expressed as the sum of ozone-depleting potential, ODP in kg CFC 11-equivalents, 20 years). Acidification of land and water sources. Emission of acidifying gases (expressed as the sum of acidifying potential, AP in kg SO2 - equivalents). Eutrophication. Emission of substances contributing to eutrophication potential, (expressed as the sum of nutrition potential, EP in kg PO4 -equivalents). Formation of photochemical oxidants. Emission of gases that contribute to the creation of ground-level ozone (expressed as the sum of ozone-creating potential, POCP, in kg C2H4-equivalents). Waste to disposal should be declared as: Hazardous waste (kg) according to EU directive 91/689/EEC and 75/442/EE. (Current regulations that apply in Norway: Regulation for recycling and treatment of waste, FOR-

15 , with amendment FOR , Ministry of Environment (Norwegian: Avfallsforskriften)). Non hazardous waste (kg) 7 Additional environmental information An EPD for solid wood product shall include the following information related to environmental issues, in addition to the environmental information derived from LCA. 7.1 Origin of round timber Environmental information about the round timber origin shall be reported, that is the amount of round timber that comes from PEFC or FSC certified forestry or similar certification systems, the extent of Chain of Custody certification or any environmental requirement for timber trade. 7.2 Chemicals Specification of materials and substances that can adversely affect human health and the indoor environment in all stages of the life cycle shall be reported. A detailed list of the product s substances (chemicals used in manufacture), including CAS number and health class (Risk phrases), shall be included in the product content declaration. The content of substances shall be declared in weight %. In cases where information about contents could affect patent or company secrets, a qualitative list of chemicals and their expected functions is sufficient, including the Risk phrases Health and environmental risk impact from chemicals (optional) The health risk impacts shall be calculated according to the rules developed in the project Environmental Product Declaration (EPD) as a tool for documentation/information on chemicals and toxicity in the value chains of products a pre-study for EPD-Norway. The calculation methods for calculating the health risk impact and environmental impact are described in Appendix 2 and the results are preliminarily classified in 6 classes. Since the working environment is not included in ISO Environmental declaration of building products, the working environment will not be included in the EPD for building materials. Such calculation may be carried out in the company s Environmental Management System. The working environment is normally regulated by national legislation Indoor environment impact Impact on the indoor environment may be provided as additional environmental information. In that case, it could be classified according to the M1 method. The calculation method for calculating indoor environmental impact is described in Appendix 3.

16 Other additional environmental information A description of toxicity effects occurring in the use of the product, such as leaching Calorific value and moisture content of wood fuels used in the energy consumption calculations Relevant information, such as specific manufacturing processes, with an effect on environment Technical data that is needed to model the use stage (e.g. load requirements) 8 Content of the environmental declaration (EPD) All Type III environmental declarations in a product category shall follow the format and include the parameters as identified in this PCR. 8.1 General information to be declared The following general information shall be declared: the name and address of the manufacturer(s). product identification by name (including e.g. production code) and a simple visual representation of the building product to which the EPD is developed. the description of the product s use and the functional or declared unit of the product to which the data relates. the description of the application (installation) of the wood product. a general specification for the composition of the products shall be given. name of the programme and the programme operator s address and, if relevant the logo and website. the PCR identification. the date the declaration was issued and period of validity. additional environmental information. a statement of whether the declaration is complete or modular (ISO 21930) a statement that environmental declarations from different programmes (ISO 14025) may not be comparable. a statement that the declaration represents an average performance, in such cases where an EPD declares an average performance for a number of products. In addition the standard deviation of the products performance with respect to the average is stated. the site(s), manufacturer or group of manufacturers or those representing them for whom the results of the LCA are representative. information on where explanatory material may be obtained. in addition to the above, Table 6 shall be completed and reproduced in the Type III environmental declaration.

17 17 Table 6 Demonstration of verification PCR review, was conducted by: < name and organization of the chair, and information on how to contact the chair through the programme operator > Independent verification of the declaration and data, according to ISO 14025: internal external (Where appropriate a ) Third party verifier: <name of the third party verifier> a Optional for business to business communication, mandatory for business to consumer communication. a diagram of the life cycle stages included in the LCA subdivided into product stage, building stage and end of life stage, and system boundaries. The stages may be further subdivided, see ISO Fig 1. a description of the nature of the processes and ancillary materials that are required for installing the building product in the building works and their replacement and maintenance according to the cut-off criteria in the PCR see chapter Period of validity of the document This document is valid until September 2012 (3 years).

18 18 10 References 1. ISO Sustainability in building construction - Environmental declaration of building products 2. ISO Environmental labels and declarations Type III environmental declarations Principles and procedures 3. ISO Environmental management - life cycle assessment - requirements and guidelines 4. Energi- og miljøregnskap for bygg. Prosjektrapport 173. Byggforsk ISO Environmental management Specification of the requirements of an environmental management system (EMS) 6. EMAS The Eco-Management and Audit System Specification of the requirements of an environmental management system (EMS) 7. ISO Buildings and constructed assets Service life planning Part 8: Reference service life 8. PCR 2006:02, Product-category Rules (PCR) for preparing an environmental product declaration (EPD) for Building products, The Swedish Environmental Management Council PSR 1999:1 Produktspecifika utgångspunkter Sågade trävaror, AB Trätek NPCR 014, Product-catagory rules (PCR) for Preparing an Environmental Declaration (EPD) for Product Group Windows and Doors, SINTEF Byggforsk Aasestad, K The Norwegian Emission Inventory Documentation of methodologies for estimating emissions of greenhouse gases and long-range transboundary air pollutants. Statistisk sentralbyrå. Reports 2008/48: 252 pp. 12. Treteknisk Håndbok, Norsk Treteknisk Institutt, ISBN , May 2009 Approved , valid until Norwegian EPD Foundation, PCR Review Panel Panel chairman

19 19 Appendix 1 Project documentation/report Project documentation shall include information, which can be made available to verifier in order to demonstrate that the requirements of ISO Environmental declaration of building products have been met: the input and output environmental data of the unit processes that are used for the LCA calculations; the documentation (measurements, calculations, estimates, sources, correspondence, traceable references to origin, etc) that provides the basis from which the process data for the LCA is formulated; This includes documentation on: the specification used to create the manufacturer's products; energy consumption figures; emission data to air, water and soil; waste production; data that demonstrates that the information is complete. In specific cases, reference can be made to, for instance, standards or quality regulations; referenced literature and databases from which data have been extracted; documentation that demonstrates that the products can fulfil the desired function(s) and performance; documentation that demonstrates that the chosen processes and scenarios in the flow chart satisfy the requirements set in ISO 21930; documentation that substantiates the chosen life cycle of the products; the documentation and substantiation of the percentages or figures used for the calculations in the waste scenario; documentation and substantiation of the percentages and figures (number of cycles, prices, etc.) used for the calculations in the allocation procedure; information showing how averages of different reporting locations have been calculated in order to obtain generic data; documentation used to substantiate any qualitative information in the additional environmental information; procedures used to carry out the data collection (questionnaires, instructions, informative material, confidentiality agreements, etc.); the characterization factors, normalisation factors and weighting factors used; the criteria and substantiation used to determine the system limits and the selection of input and output flows; documentation used to substantiate the other choices and assumptions

20 20 Appendix 2 chemicals Health and environmental risk impact from Classification of health impact: Class Impact Risk phrases Weight (g)/fu Class 1 CMR substances. Need authorisation R 40, 45, 46, 49, 60, 61, 62, 63 according to REACH Class 2 Chemicals that are very toxic may R 26, 27, 28, 39, 42, 64 sensitise by inhalation. Danger of very serious irreversible effects or damage breastfed children Class 3 Chemicals that are toxic may sensitise by skin contact, very corrosive, danger of serious damage to health by prolonged exposure. R 23, 24, 25, 35, 48, 68, (YL-gr 4-5) Class 4 Harmful, corrosive, danger of cumulative effects. May cause lung damage if swallowed, vapour may cause drowsiness and dizziness. R 20, 21, 22, 33, 34, 41, 65, 67 (Yl-gr 2-3) Class 5 Irritants R 36, 37, 38, 66 (YL-gr 00-1) Class 6 No classified due to health effects Classification of environmental impact: Class Impact Risk phrases Weight (g)/fu Class 1 PBT, vpvb and other substances which need authorisation according to REACH* Class 2 Very toxic and may cause long term R50/53 adverse effects Class 3 Toxic and may cause long term R51/53 adverse effects; Class 4 Harmful and may cause long term R52/53 adverse effects Class 5 Toxic/harmful or may cause long term adverse effects R50, R51, R52, R53, R54, R55, R56, R57, R58, R59 Class 6 No classified due to environmental effects *(PBT) persistent, bio-accumulative and toxic substances, (vpvb) very persistent and very bio-accumulative substances

21 21 Appendix 3 Indoor environment impact M1 Emission classification of building materials This scheme is well established in the Finnish market. It was published for the first time in 1995 by the Finnish Society for Indoor Air Quality (FISIAQ) under the title Classification of Indoor Climate, Construction and Finishing Materials. The first products were labelled in In May 2000, the name changed into Emission classification of building materials and at the present the scheme forms a part of a larger system with the aim of obtaining good indoor climate quality for the whole of the buildings in this scheme, good indoor climate quality is defined by means of S1 to S3 values in the Indoor Climate 2000 classification [22]. Currently, the scheme is operated by The Building Information Foundation (RTS) which has close contact with the building industry. The materials are labelled M1, M2, and M3 where M1 represents materials of low emission and M3 represents materials with the highest emissions. All information about Emission classification of building materials is available at with a list of all materials that are labelled M1. For materials in the M1 group, the following requirements apply: Test requirement after 28 days TVOC < 200 µg/m 2 h Carcinogenic compounds Cat. 1< 5 µg/m 2 h Sensory effect Dissatisfaction concerning odour < 15 % in climpaq test Formaldehyde < 50 µg/m 2 h Ammoniac < 30 µg/m 2 h Casein Not permitted Table 1: Assessment requirements for M1 classification in Emission classification of building materials

22 22 Appendix 4 Standards of relevance for solid wood products Document Title Pub. Year Planed timber EN Wood flooring - Solid softwood floor boards 2004 EN Wood flooring - Characteristics, evaluation of conformity and marking 2005 EN Solid softwood panelling and cladding - Machined profiles with tongue and 2005 groove EN Solid wood panelling and cladding - Characteristics, evaluation of conformity 2007 and marking EN Solid softwood panelling and cladding - Machined profiles without tongue and 2006 groove SN TS 3183 Technical specification for interior soft wood panels SN TS 3186 Technical specification for exterior soft wood cladding 2008 NS 3184 Høvellast - Glattkant 1976 NS 3187 Høvellast - Innvendig listverk av tre 1981 Timber structures EN Timber structures - Glued laminated timber - Requirements 2005 EN Timber structures - Strength graded structural timber with rectangular cross 2006 section INSTA 142 Nordiske regler for visuell styrkesortering av trelast 1997 Other EN Durability of wood and wood-based products - Definition of use classes 2006 EN Round and sawn timber. -Terminology 1995 EN 1310 Round and sawn timber - Method of measurement of features 1997 EN Round and sawn timber - Permitted deviations and preferred sizes - Part 1: 1997 Softwood sawn timber EN Sawn timber - Appearance grading of softwoods - European spruces, firs, 1999 pines, Douglas fir and larches NS 3079 Trelast - Dimensjoner 1980 Further European standards can be found at