1114 Ver. 2:214 ENVIRONMENTAL PRODUCT DECLARATION In accordance with ISO 1425 ISO 2193 EN 1584 Publisher Declaration number Issue date Valid to Norgips Windliner-X/Utvendig-X type EH2 (GU-X) Product The Norwegian EPD Foundation NE EN, updated..2..2 2 NEPD-19-177-EN, updated, Norgips Windliner-X/Utvendig-X type EH2 (GU-X)
General information Product Norgips Windliner-X/Utvendig-X type EH2 (GU-X) Contact person: Johan Arvidsson Phone: +47337848 Johan.Arvidsson@norgips.com Program holder The Norwegian EPD Foundation Post Bo 525 Majorstuen, 33 Oslo Manufacturer Postboks 655 Strømsø Phone: +47 23 8 8 33 Drammen post@epd-norge.no Declaration number: NE EN, Place of production:, Svelvik This declaration is based on Product Category Rules: EN 1584:212+A1:213 serve as core PCR NPCR 1:213 rev 1, PCR for Building boards Declared unit: Management system: Org. No: NO 98634757 MVA Declared unit with option: Issue date Functional unit: 1 m 2 of installed plasterboard used for walls, during 6 years The EPD has been worked out by: Mie Vold Verification: Independent verification of data, other environmental information and EPD has been carried out in accordance with ISO1425, 8.1.3 and 8.1.4 eternally internally Valid to Comparability: EPD of construction products may not be comparable if they not comply with EN 1584 and seen in a building contet. Year of study: 214 Approved sign <Title Name> Independent verifier approved by EPD Norway Functional unit 1 m 2 of installed plasterboard used for walls, during 6 years Unit Cradle to gate Key environmental indicators A1-A3 Global warming CO 2 -eq. 1,8 Energy use 34,6 Dangerous substances * 7, Recycled raw materials % 97,9 A4,29 4,5 Module D MND * The product contains no substances from the REACH Candidate list or the Norwegian priority list NEPD-19-177-EN, updated, Norgips Windliner-X/Utvendig-X type EH2 (GU-X) 2/7
Product Product description: Gypsum plasterboard composed of a plaster core encased in and firmly bonded to paper liners. The front and back paper liners are overlapped and glued together on the backside of the board. The front paper, colored in red, is impregnated with a natural preservative that makes the surface water repellent. For use as wind sheathing board and wind bracing. Technical data: The product is in compliance with EN 52 Weight: 7,2 /m 2 ± 2 % Thickness: 9,5 mm ±,5 mm For more information from the product data sheet, see www.norgips.no / www.norgips.se Market: Norway and Sweden Product specification Materials (ecl water) % Gypsum (REA) 6,7 93, Cardboard,4 4,9 Glass fibre reinforcement Div additives (total),15 2,1 Totalt 7,2 1 Reference service life: 6 years LCA: Calculation rules Functional unit: 1 m 2 of installed plasterboard used for walls, during 6 years System boundary: Industrial gypsum and recycled gypsum are mied and dried before the miture is calcined. The calcined gypsum is transferred to the mier where water and additives are added. The slurry is distributed to a plasterboard liner where the edges are folded and a new layer of plasterboard liner is glued on to form a sandwich. The board line is continuous transferred along the production line, cut to suitable lengths and dried in a kiln. The dried boards are cut to the correct lengths and stacked in pallets. Scenarios for user phase (B1-B7) and end of life (C1-C4) are decribed in scenarios below Data quality: Specific data for products and mass flows are from 213. Data sources: Ecoinvent 2.2/SimaPro software (generic). Ecoinvent 2.2 processes are created 23-27. Upstream data for raw materials are significant for the LCA results in this study; these are modelled using Ecoinvent processes. EcoInvent 2.2 is used since EcoInvent 3 had important data gaps when the assessment was completed. Impact assessment methods are in accordance with EN 1584:212 + A1:213 Allocation: The allocation is made in accordance with the provisions of EN 1584. Incoming energy and water and waste production in-house production is allocated equally among all products through mass allocation. Effects of primary production of recycled materials allocated to the main product in which the material was used. The recycling process and transportation of the material is allocated to this analysis. Cut-off criteria: All major raw materials and all the essential energy is included. Also production processes for raw materials and energy flows that are included with very small amounts (<1%) are included. NEPD-19-177-EN, updated, Norgips Windliner-X/Utvendig-X type EH2 (GU-X) 3/7
LCA: Scenarios and additional technical information The following information describe the scenarios in the different modules of the EPD. from production place to user (A4) of building products from manufacturer to building site (distance estimated to 36 km) Type Capacity utilisation (incl. return) Type of vehicle Distance km Fuel/Energy % consumption Truck Average European capacity utilisation Lorry >32 metric ton 36,2 l/tkm Railway kwh/tkm Boat l/tkm Value (l/t) 7,6 Installation in the building (A5) Data on energy consumption on the building site is based on lifting the board into the building information given by. An average energy consumption value of,121 /m² (3*1-4 kwh/m 2 ) shall be applied. It is assumed 5% loss in implementation. Auiliary Water consumption Electricity consumption Other energy carriers Material loss Output materials from waste treatment Dust in the air UnitValue m 3 kwh 3E-4,36 User phase B1-B7 All modules in user phase have been assessed, but the product will not need maintenance, repair or replacement during the user phase. Therfor the environmental impact for the user phase is zero. Replacement cycle* Electricity consumption Replacement of worn parts Unit kwh Value 1 * Number or RSL (Reference Service Life) End of Life (C1, C3, C4) When the product is discarded and its original function is lost, it can be processed further in a waste management system. The flows of the recycled material will then become inputs into the production of the net product. For Norgips building boards it has been assumed that 4 % of all materials from demolition will be reused/recycled and the rest will be sent to disposal. Hazardous waste disposed Collected as mied construction waste Reuse Recycling Energy recovery To landfill Unit Value 2,9 4,3 to waste processing (C2) Type Capacity utilisation (incl. return) % Type of vehicle Distance km Fuel/Energy consumption Truck Average European capacity utilisation Lorry >32 metric ton 5,2 /tkm Railway kwh/tkm Boat l/tkm Value (l/t) 1,2 NEPD-19-177-EN, updated, Norgips Windliner-X/Utvendig-X type EH2 (GU-X) 4/7
LCA: Results All modules from rawmaterial production to end of life are included. The modules in user phase have no impacts since nothing happens during user phase. System boundaries (X=included, MND=module not declared, MNR=module not relevant) Product stage Construction installation stage Use stage End of life stage Beyond the system boundaries Raw materials Manufacturing Construction installation stage Use Maintenance Repair Replacement Refurbishment Operational energy use Operational water use De-construction demolition Waste processing Disposal Reuse-Recovery- Recycling-potential A1 A2 A3 A4 A5 B1 B2 B3 B4 B5 B6 B7 C1 C2 C3 C4 D MND Environmental impact Parameter Unit GWP CO 2 -eq. ODP CFC11 -eq. POCP C 2 H 4 -eq. AP SO 2 -eq. Resource use Parameter RPEE RPEM TPE NRPE NRPM TRPE SM RSF NRSF W 1,2E-7 2,1E-4 1,6E-3 4,7E-8 3,8E-5 3,1E-4 9,E-13 1,8E-9 1,6E-8 EP PO 3-4 -eq. 3,7E-3 1,1E-3 3,7E-8 3,7E-8 1,2E-4 1,8E-4 ADPM Sb-eq. 1,3E-6 8,7E-7 4,3E-11 4,3E-11 1,1E-7 3,3E-8 ADPE 32 4,3 1,3E-4 1,3E-4,58,76 GWP Global warming potential; ODP Depletion potential of the stratospheric ozone layer; POCP Formation potential of tropospheric photochemical oidants; AP Acidification potential of land and water; EP Eutrophication potential; ADPM Abiotic depletion potential for non fossil resources; ADPE Abiotic depletion potential for fossil resources Unit A1-A3 1,8 A4,29 A5 1,2E-5 B1-B7 End of life - Waste Parameter Unit A1-A3 A4 A5 B1-B7 C1 C2 C3 HW 3,4E-5 5,1E-6 4,6E-1 4,6E-1 6,8E-7 NHW 2,3,52 1,5E-5 1,5E-5 6,9E-3 RW N/A N/A N/A N/A N/A N/A N/A HW Hazardous waste disposed; NHW Non hazardous waste disposed; RW Radioactive waste disposed End of life - Output flow Parameter Unit A1-A3 A4 A5 B1-B7 C1 C2 C3 C4 CR MR 1,4 2,9 MER 1,3E-5 EEE ETE CR Components for reuse; MR Materials for recycling; MER Materials for energy recovery; EEE Eported electric energy; ETE Eported thermal energy C1 1,2E-5 9,E-13 1,8E-9 1,6E-8 C2,39 6,3E-9 5,E-6 3,3E-5 C3 C4,31 A1-A3 A4 A5 B1-B7 C1 C2 C3 C4 2,5,25,61 6,3E-3 1,2E-3 3,9E-5 1,2E-3 3,9E-5 8,1E-3 8,3E-4 6,3E-3 6,3E-4 2,7,68 1,3E-3 1,3E-3 9,E-3 7,E-3 32 4,4 1,7E-4 1,7E-4,59,77,49 33 4,4 1,7E-4 1,7E-4,59,77 7,6-4,E-3 m 3,11 9,1E-5 1,4E-3 1,9E-7 1,8E-4 RPEE Renewable primary energy resources used as energy carrier; RPEM Renewable primary energy resources used as raw materials; TPE Total use of renewable primary energy resources; NRPE Non renewable primary energy resources used as energy carrier; NRPM Non renewable primary energy resources used as materials; TRPE Total use of non renewable primary energy resources; SM Use of secondary materials; RSF Use of renewable secondary fuels; NRSF Use of non renewable secondary fuels; W Use of net fresh water 9,2E-9 6,7E-6 4,5E-5 C4 3,1E-7 4,3 N/A Reading eample: 9, E-3 = 9,*1-3 =,9 NEPD-19-177-EN, updated, Norgips Windliner-X/Utvendig-X type EH2 (GU-X) 5/7
Additional Norwegian requirements Electricity The following data from ecoinvent v2 for Norwegian production mi included import,electricity, medium voltage, at grid/kwh/no/s. import, production of transmission lines, in addition to direct emissions and loss in grid are included. Characterisation factors stated in EN 1584:212+A1:213 are used. Greenhouse gas emissions: 36 g CO 2 - eq./kwh Dangerous substances None of the following substances have been added to the product: Substances on the REACH Candidate list (per 17.12.214) of substances of very high concern or substances on the Norwegian Priority list (per 4.12.214) or substances that lead to the product being classified as hazardous waste. The chemical content of the product complies with regulatory levels as given in the Norwegian Product Regulations. to building site is inn accordance with scenario description A4 36 km Indoor environment TVOC <1 µg/m 2 h Measured after 3 days Formaldehyde <1 µg/m 2 h Ammonia 22 µg/m 2 h Carcinogenic compounds <2 µg/m 2 h Classified as category M1 Classification according to EN 15251:27 Noise No information db(a) * Emissions are measured for Norgips Plasterboard 13 Type A (STD), report from SP 23.1.29 Carbon footprint Carbon footprint has not been worked out for the product. Bibliography ISO 1425:26 Environmental labels and declarations - Type III environmental declarations - Principles and procedures ISO 1444:26 Environmental management - Life cycle assessment - Requirements and guidelines EN 1584:212 + A1:213 Sustainability of construction works - Environmental product declaration - Core rules for the product category of construction products ISO 2193:27 Sustainability in building construction - Environmental declaration of building products PCR NPCR 1:213 rev 1, PCR for Building boards, www.epd-norge.no Vold, M, 214 Livsløpsdata for Gipsplater fra Norgips, Barunnsdata for miljødeklarasjon (EPD),Østfoldforskning, OR 27.14, Fredrikstad NEPD-19-177-EN, updated, Norgips Windliner-X/Utvendig-X type EH2 (GU-X) 6/7
Program holder and publisher The Norwegian EPD Foundation Post Bo 525 Majorstuen, 33 Oslo Norway Postboks 655 Strømsø 33 Drammen Author of the Life Cycle Assessment Mie Vold Ostfoldforskning AS Stadion 4, 1671 Kråkerøy NEPD-19-177-EN, updated, Norgips Windliner-X/Utvendig-X type EH2 (GU-X) Phone: +47 23 8 8 web Phone: Fa web Phone: Fa web post@epd-norge.no www.epd-norge.no +47 33 78 48 norgips@norgips.com www.norgips.no +47 414 69 8 +47 69 34 24 94 mie@ostfoldforskning.no www.ostfoldforskning.no 7/7