ENVIRONMENTAL PRODUCT DECLARATION
as per ISO 14025 and EN 15804
Owner of the Declaration
dormakaba International Holding GmbH
Programme holder
Institut Bauen und Umwelt e.V. (IBU)
Publisher
Institut Bauen und Umwelt e.V. (IBU)
Declaration number
EPD-DOR-20200269-IBA1-EN
Issue date
28.06.2021
Valid to
27.06.2026
ES PROLINE
Modular Automatic Drive System for Sliding Doors
dormakaba
Website
1. General Information
[dormakaba logo]
Programme holder
IBU - Institut Bauen und Umwelt e.V.
Panoramastr. 1
10178 Berlin
Germany
Declaration number
EPD-DOR-20200269-IBA1-EN
This declaration is based on the product category rules:
Drive systems for automatic doors and gates, 11.2017 (PCR checked and approved by the SVR)
Issue date
28.06.2021
Valid to
27.06.2026
[Signature of Dipl. Ing. Hans Peters, chairman of Institut Bauen und Umwelt e.V.]
[Signature of Dr. Alexander Röder, Managing Director Institut Bauen und Umwelt e.V.]
Owner of the declaration
dormakaba International Holding GmbH
DORMA Platz 1
58256 Ennepetal
Germany
Declared product / declared unit
ES PROLINE - Modular Automatic Drive System for Sliding Doors
Scope:
This EPD refers to the entire life cycle of a representative ES PROLINE drive system. The various technical characteristics are depicted in section 2.3. The production location is the DORMA production site in Ennepetal, Germany. The material and energy flows were taken into consideration accordingly.
The owner of the declaration shall be liable for the underlying information and evidence; the IBU shall not be liable with respect to manufacturer information, life cycle assessment data and evidences.
Verification
The standard EN 15804 serves as the core PCR
Independent verification of the declaration and data according to ISO 14025:2010
Verification status: ✔️ internally ❌ externally
[Signature of Dr.-Ing. Wolfram Trinius, Independent verifier appointed by SVR]
2. Product
2.1 Product description/Product definition
With ES PROLINE, a drive system has been developed that offers the latest dormakaba technology. At the same time, the drive meets high design and functional requirements of modern buildings. The ES PROLINE drive system offers versatile application possibilities. It does not matter whether it is a standard door, a door in escape and rescue routes or a telescopic sliding door. Even particularly heavy door leaves are no problem for the drive. Up to 400 kg can be moved with the new system.
With the following ES PROLINE drive system variants you can meet almost all requirements:
- ES 250: Standard doors
- ES 250 PRO FST: Escape and rescue routes
- ES 250 PRO EASY: Standard doors, less features
- ES 400 PRO / ES 400 PRO FST: For heavy standard doors and escape and rescue routes optional with Resistance Class (RC)
The product family of the modular automatic ES PROLINE drive system covers all above mentioned drive systems. The configuration of the drive is modular. Additional modules can be added like battery packs and interlocks. Values (material and energy flows) for a representative product are based on the volumes of ES PROLINE variants sold during the reference period.
For the placing on the market in the European Union/European Free Trade Associaton (EU/EFTA) (with the exception of Switzerland) the following legal provisions apply:
- Machinery Directive 2006/42/EC
- 2014/30/EU Electromagnetic Compatibility Directive
2.2 Application
The automatic ES PROLINE drive system is used as a drive for automating sliding door systems as well as escape and rescue routes:
Door parameter | Use in escape and rescue routes | ES PROLINE variants | |||
---|---|---|---|---|---|
ES 250 PRO | ES 250 PRO FST | ES 250 PRO EASY | ES 400 PRO / ES 400 PRO FST | ||
Opening width (mm) | Single-panel sliding door | 700-3000 mm | 700-3000 mm | 800-3000 mm | 800-3000 mm |
Double-panel sliding door | |||||
Door panel weight max. (kg) | 1x125kg | 1x250 kg | 2x125 kg | 2x200 kg |
Technical specifications:
- Hold open time ES PROLINE: 0 - 180 s
- Supply voltage, frequency ES PROLINE: 50 - 60 Hz
- Power input ES PROLINE: 130 - 180 W
- Protection type IP: 120
- Low-voltage and EMC Directives
Product not harmonised in accordance with the CPR but in accordance with other provisions for harmonisation of the EU:
- Machinery Directive 2006/42/EC
- 2014/30/EU Electromagnetic Compatibility Directive
- 2011/65/EU ROHS3 Directive
- DIN EN ISO 12100:2011-03 Safety of machinery
- DIN EN 16005: 2013-01 and Amendment 2015-10 Power operated pedestrian doorsets
- DIN EN ISO 13849- 1:2016-06 Safety of machinery
- DIN EN ISO 13849- 2:2013-02 Safety of machinery
- DIN EN 60335-2-103: 2016-05 Household and similar electrical appliances
- DIN EN 61000-3-2:2015-03 Electromagnetic compatibility (EMC)
- DIN EN 61000-6-2: 2005 and Amendment:2011 Electromagnetic Compatibility (EMC)
The CE-marking takes into account the proof of conformity with the respective harmonized standards based on the legal provisions above.
2.3 Technical Data
The following technical data is of relevance for the LCA:
Constructional data
Name | Value | Unit |
---|---|---|
Height | 100 | mm |
Installation depth | 180 | mm |
Opening and closing force | 150 | N |
Opening speed ES 250 PRO | 10 - 70 | cm/s |
Opening speed ES 400 PRO | 10 - 90 | cm/s |
Opening speed ES 250 PRO EASY | 10 - 70 | cm/s |
Opening speed ES 250 PRO FST | 20 - 70 | cm/s |
Opening speed ES 400 PRO FST | 20 - 90 | cm/s |
Closing speed ES 250 PRO | 10 - 70 | cm/s |
Closing speed ES 400 PRO | 10 - 90 | cm/s |
Closing speed ES 250 PRO EASY | 10 - 70 | cm/s |
2.4 Delivery status
One automatic ES PROLINE drive system (representative by sales volume) has the following delivery status:
Components | Absolute | Percentage |
---|---|---|
Average ES PROLINE | 24.47 kg | 89% |
Average Packaging | 3.00 kg | 11% |
Total | 27.47 kg | 100% |
2.5 Base materials/Ancillary materials
The ES PROLINE family comprises the following components:
Components | Percentage |
---|---|
Aluminum elements | 52% |
Steel elements | 30% |
Plastic elements | 7% |
Electronic elements | 4% |
Other | 6% |
Total | 100% |
The products include partial articles which contain substances listed in the candidate list of REACH Regulation 1907/2006/EC (date: 19.01.2021) exceeding 0.1 percentage by mass: ✔️ yes ❌ no
- Lead (Pb): 7439-92-1 (CAS-No.) is included in some of the alloys used. The concentration of lead in each individual alloy does not exceed 4.0% (by mass).
This product/article/at least one partial article contains other carcinogenic, mutagenic, reprotoxic (CMR) substances in categories 1A or 1B which are not on the candidate list, exceeding 0.1 percentage by mass: ❌ no.
Biocide products were added to this construction product or it has been treated with biocide products (this then concerns a treated product as defined by the (EU) Ordinance on Biocide Products No. 528/2012): ❌ no.
2.6 Manufacture
The drive units and requisite circuit boards of ES PROLINE product family are manufactured at dormakaba. The certified Quality Management system in accordance with ISO 9001 safeguards the high-quality standard of dormakaba products. It guarantees continuous improvement of the overall processes and product quality at the dormakaba locations.
2.7 Environment and health during manufacturing
No health protection measures beyond the legally specified measures are required. The maximum allowable concentrations are clearly complied with at each point of production.
- Air: Waste air generated during production is cleaned in accordance with statutory specifications. Emissions are significantly below the Technical Instructions on Air Quality.
- Water/Ground: No contamination of water or ground. Production-related waste/ water is treated internally and redirected to the production process.
- Sound protection: Analyses have established that all values communicated inside and outside the production facilities are far below the standards applicable in Germany.
The Environmental Management system in the dormakaba production facility Ennepetal is certified to ISO 14001; industrial safety is certified to OHSAS 18001.
2.8 Product processing/Installation
dormakaba sliding door drives are installed by specially-trained assembly teams to install the drives or the product system.
2.9 Packaging
The declared unit includes the following packaging materials and their percentages by mass:
Components | Percentage |
---|---|
Paper and Cardboard | 99% |
Foil | 1% |
Total | 100% |
More information on the possible re-use of packaging is provided in section 2.14 and 2.15.
2.10 Condition of use
No auxiliaries or consumables are incurred during maintenance, and use of the automatic drive system ES PROLINE. Regular maintenance is advised to ensure the service life of 15 years. For repairs or renewals, suitable spare parts are available. The energy supply for the analysed drive units has been calculated for the reference service life of 15 years.
2.11 Environment and health during use
There are no known impact relations between product, environment and health during use.
2.12 Reference service life
The reference service life amounts to 15 years. This complies with 1,500,000 cycles according to EN 16005.
2.13 Extraordinary effects
Fire
Due to the predominant use of aluminium and steel which are considered non-flammable or flame-retardant, no additional influence on the environment in case of fire is to be expected.
Fire protection | Value |
---|---|
Building material class | not applicable |
Burning droplets | not applicable |
Smoke gas development | not applicable |
Water
No negative impact on the ecological water quality is expected by contact of the product with water.
Mechanical destruction
No impacts on the environment are expected in the case of an unforeseeable mechanical destruction.
2.14 Re-use phase
With reference to the material composition of the product system in accordance with section 2.6, the following possibilities arise:
- Re-use: During refurbishment or de-construction, the drive system can be easily segregated and re-used for the same application.
- Material recycling: The metallurgical materials contained in the product are suitable for material recycling.
- Energy recovery: The plastics contained in the product are suitable for energetic recovery.
- Landfilling: Is not applicable.
2.15 Disposal
Cuttings:
Cuttings incurred during the manufacturing phase are directed towards metallurgical recycling and energy recovery. Cuttings are collected separately and collected by a disposal company.
Following European Waste Catalogue (EWC) Codes are relevant:
- EWC 07 02 03 Plastic waste
- EWC 12 01 01 Ferrous metal filings and turnings
- EWC 12 01 03 Non-ferrous metal filings and turnings
Packaging:
Packaging incurred for installation in the building is directed towards energy recovery.
- EWC 15 01 01 Paper and cardboard packaging
- EWC 15 01 02 Plastic packaging
End of Life:
All materials are directed to an energy recovery or recycling process.
- EWC 16 02 14 Used devices with the exception of those included in 16 02 09 to 16 02 13
- EWC 16 02 16 Components removed from used devices with the exception of those included in 16 02 15
- EWC 17 02 03 Plastic
- EWC 17 04 02 Aluminum
- EWC 17 04 05 Iron and steel
- EWC 17 04 11 Cables with the exception of those included in 17 04 10
Disposal of the drive unit in Europe is subject of the WEEE Guideline 2002/96/EC.
2.16 Further information
Contact data for more detailed information: Please refer to the last page of this Declaration.
3. LCA: Calculation rules
3.1 Declared Unit
The declaration represents one (1) ES PROLINE.
Name | Value | Unit |
---|---|---|
Declared unit | 1 | pce. |
Conversion factor to 1 kg | 0.036 | - |
3.2 System boundary
Type of the EPD: cradle to gate - with options
Modules A1-A3, A4, and A5
The product stage (A1-A3) begins with considering the production of the necessary raw materials and energies, including all corresponding upstream chains and the actual procurement transports. Furthermore, the entire manufacturing phase was mapped, including the treatment of production waste until the end-of-waste status (EoW) was reached. In addition, both the distribution transports (A4) and the installation including power-consuming tools, installation materials and the packaging waste generated during installation (A5) were taken into account.
Module B6
Module B6 includes the operational energy use over the service life of 15 years.
Modules C1-C4
The modules include the environmental impacts for dismantling of the ES PROLINE and the treatment of the waste categories until end-of-waste status (EoW) is reached, including the associated transports at the end of the product life cycle.
3.3 Estimates and assumptions
It was assumed that End-of-Life thermal waste incineration plants are plants with an R1 factor (energy conversion efficiency or energy efficiency of waste incineration plants according to the European Waste Framework Directive) >0.6.
3.4 Cut-off criteria
The effect associated with the neglected mass shares is less than 5% of the effect categories per module. The minimum limit of 1% total mass and the use of renewable and non-renewable primary energy is not exceeded.
3.5 Background data
The LCA software GaBi 9.5 was used to model the life cycle. The entire manufacturing process, as well as energy consumption, were modelled on the basis of manufacturer-specific data. However, generic background datasets were used for the upstream and downstream processes. The majority of the background datasets used were taken from the current version of the GaBi 9.5 database. Ecoinvent Version 3.6 and Ecoinvent Version 2.2 datasets were only used when suitable GaBi 9.5 datasets were not available.
Where possible, German datasets were used for modules A1-A3, and the corresponding European datasets for distribution transports (A4), installation (A5) and disposal scenarios (C modules).
3.6 Data quality
The background datasets used for accounting purposes mainly originate from the respective updated GaBi 9.5 databases at the time of calculation. The data for the examined products was captured on the basis of evaluations of internal production and environmental data, the collection of LCA-relevant data within the supply chain, as well as the evaluation of relevant data for the energy supply. The collected data were checked for plausibility and consistency. Good representativity can be assumed.
3.7 Period under review
Life cycle assessment data were collected in 2019 and 2020.
3.8 Allocation
All required energies, raw materials, and supplies could be (clearly) assigned to the declared product. No by-products are produced and no allocation is required. In module A1-A3, credits are issued for recycling of metallurgical waste. Packaging materials and the combustible product parts are incinerated at the end of life in a waste incineration plant. Metallurgical parts are recycled. Any emissions that occur are taken into account in the model. Depending on their elementary composition and the resulting heating values, recycling credits are taken into account in module D.
3.9 Comparability
Basically, a comparison or an evaluation of EPD data is only possible if all the data sets to be compared were created according to EN 15804 and the building context, respectively the product-specific characteristics of performance, are taken into account. The background database used is GaBi 9.5 Service Pack 40.
4. LCA: Scenarios and additional technical information
Transport from the gate to the site (A4)
Name | Value | Unit |
---|---|---|
Transport distance (Truck) | 674 | km |
Capacity utilisation (including empty runs) (Truck) | 55 | % |
Transport distance (Container Ship) | 5469 | km |
Assembly (A5)
Name | Value | Unit |
---|---|---|
Auxiliary (screws and screw anchors) | 0.112 | kg |
Electricity consumption | 0.021 | kWh |
Reference service life
Name | Value | Unit |
---|---|---|
Life Span according to the manufacturer | 15 | a |
Operational energy use (B6) and Operational water use (B7)
Name | Value | Unit |
---|---|---|
Electricity consumption (15 years) | 988.49 | kWh |
Assumed load of the drive system during use stage | 2 x 120 | kg |
Energy consumption under the declared load | 0.123 | Wh/cycle |
Cycle duration | 23 | seconds |
Standby | 6.6 | W |
Assumed number of annual cycles | 100,000 | cycles |
Opening width | 1600 | mm |
End of life (C1-C4)
Name | Value | Unit |
---|---|---|
Collected separately waste type | 24.58 | kg |
Collected as mixed construction waste | - | kg |
Reuse | - | kg |
Recycling | 21.12 | kg |
Energy recovery | 3.44 | kg |
Landfilling | 0 | kg |
Reuse, recovery and/or recycling potentials (D), relevant scenario information
Name | Value | Unit |
---|---|---|
Net steel scrap | 6.19 | kg |
Net aluminium scrap | 2.56 | kg |
Net zinc scrap | 0.85 | kg |
Collection rate | 100 | % |
Recycling loss | 0 | % |
5. LCA: Results
The following table shows the results of the LCA for 1 piece ES PROLINE. The results in module B6 are based on a lifetime of 15 years.
DESCRIPTION OF THE SYSTEM BOUNDARY (X = INCLUDED IN LCA; MND = MODULE NOT DECLARED; MNR = MODULE NOT RELEVANT)
PRODUCT STAGE | CONSTRUCTI ON PROCESS STAGE | USE STAGE | END OF LIFE STAGE | BENEFITS AND LOADS BEYOND THE SYSTEM BOUNDARIES | ||||||||||||
---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|
Raw material supply | Transport | Manufacturing | Transport from the gate to the site | Assembly | Use | Maintenance | Repair | Replacement | Refurbishment | Operational energy use | Operational water use | De-construction demolition | Transport | Waste processing | Disposal | Reuse- Recovery- Recycling- potential |
A1 | A2 | A3 | A4 | A5 | B1 | B2 | B3 | B4 | B5 | B6 | B7 | C1 | C2 | C3 | C4 | D |
X | X | X | X | X | MND | MND | MNR | MNR | MNR | X | MND | X | X | X | X | X |
RESULTS OF THE LCA - ENVIRONMENTAL IMPACT: 1 piece ES PROLINE
Param eter | Unit | A1-A3 | A4 | A5 | B6 | C1 | C2 | C3 | C4 | D |
---|---|---|---|---|---|---|---|---|---|---|
GWP | [kg CO2-Eq.] | 2.07E+2 | 2.77E+0 | 4.80E+0 | 3.90E+2 | 4.11E-3 | 2.14E-1 | 6.73E+0 | 0.00E+0 | -3.04E+1 |
ODP | [kg CFC11-Eq.] | 1.12E-5 | 4.10E-16 | 4.44E-15 | 1.17E-11 | 1.23E-16 | 6.81E-17 | 4.19E-14 | 0.00E+0 | -1.27E-13 |
AP | [kg SO2-Eq.] | 1.16E+0 | 4.34E-2 | 1.87E-3 | 8.19E-1 | 8.63E-6 | 9.10E-4 | 2.20E-3 | 0.00E+0 | -1.08E-1 |
EP | [kg (PO4)3--Eq.] | 6.39E-1 | 5.74E-3 | 2.95E-4 | 9.06E-2 | 9.55E-7 | 2.27E-4 | 2.28E-4 | 0.00E+0 | -6.00E-3 |
POCP | [kg ethene-Eq.] | 8.01E-2 | -7.25E-4 | 1.46E-4 | 5.83E-2 | 6.15E-7 | -3.43E-4 | 8.85E-5 | 0.00E+0 | -9.56E-3 |
ADPE | [kg Sb-Eq.] | 5.58E-2 | 1.61E-7 | 1.71E-5 | 1.30E-4 | 1.37E-9 | 2.01E-8 | 9.89E-7 | 0.00E+0 | -3.09E-3 |
ADPF | [MJ] | 2.65E+3 | 3.61E+1 | 7.29E+0 | 4.32E+3 | 4.56E-2 | 2.92E+0 | 3.77E+0 | 0.00E+0 | -3.41E+2 |
Caption: GWP = Global warming potential; ODP = Depletion potential of the stratospheric ozone layer; AP = Acidification potential of land and water; EP = Eutrophication potential; POCP = Formation potential of tropospheric ozone photochemical oxidants; ADPE = Abiotic depletion potential for non-fossil resources; ADPF = Abiotic depletion potential for fossil resources
RESULTS OF THE LCA - RESOURCE USE: 1 piece ES PROLINE
Parameter | Unit | A1-A3 | A4 | A5 | B6 | C1 | C2 | C3 | C4 | D |
---|---|---|---|---|---|---|---|---|---|---|
PERE | [MJ] | 3.80E+2 | 1.23E+0 | 3.87E+1 | 3.10E+3 | 3.27E-2 | 1.71E-1 | 8.78E-1 | 0.00E+0 | -1.32E+2 |
PERM | [MJ] | 3.77E+1 | 0.00E+0 | -3.77E+1 | 0.00E+0 | 0.00E+0 | 0.00E+0 | 0.00E+0 | 0.00E+0 | 0.00E+0 |
PERT | [MJ] | 4.18E+2 | 1.23E+0 | 1.02E+0 | 3.10E+3 | 3.27E-2 | 1.71E-1 | 8.78E-1 | 0.00E+0 | -1.32E+2 |
PENRE | [MJ] | 2.90E+3 | 3.62E+1 | 8.22E+0 | 7.00E+3 | 7.37E-2 | 2.93E+0 | 9.30E+1 | 0.00E+0 | -3.97E+2 |
PENRM | [MJ] | 8.93E+1 | 0.00E+0 | -3.44E-1 | 0.00E+0 | 0.00E+0 | 0.00E+0 | -8.89E+1 | 0.00E+0 | 0.00E+0 |
PENRT | [MJ] | 2.99E+3 | 3.62E+1 | 7.88E+0 | 7.00E+3 | 7.37E-2 | 2.93E+0 | 4.13E+0 | 0.00E+0 | -3.97E+2 |
SM | [kg] | 1.43E+1 | 0.00E+0 | 0.00E+0 | 0.00E+0 | 0.00E+0 | 0.00E+0 | 0.00E+0 | 0.00E+0 | 9.60E+0 |
RSF | [MJ] | 0.00E+0 | 0.00E+0 | 0.00E+0 | 0.00E+0 | 0.00E+0 | 0.00E+0 | 0.00E+0 | 0.00E+0 | 0.00E+0 |
NRSF | [MJ] | 0.00E+0 | 0.00E+0 | 0.00E+0 | 0.00E+0 | 0.00E+0 | 0.00E+0 | 0.00E+0 | 0.00E+0 | 0.00E+0 |
FW | [m³] | 6.51E+0 | 1.45E-3 | 1.36E-2 | 3.59E+0 | 3.78E-5 | 1.84E-4 | 1.85E-2 | 0.00E+0 | -3.61E-1 |
Caption: PERE = Use of renewable primary energy excluding renewable primary energy resources used as raw materials; PERM = Use of renewable primary energy resources used as raw materials; PERT = Total use of renewable primary energy resources; PENRE = Use of non-renewable primary energy excluding non-renewable primary energy resources used as raw materials; PENRM = Use of non-renewable primary energy resources used as raw materials; PENRT = Total use of non-renewable primary energy resources; SM = Use of secondary material; RSF = Use of renewable secondary fuels; NRSF = Use of non-renewable secondary fuels; FW = Use of net fresh water
RESULTS OF THE LCA – OUTPUT FLOWS AND WASTE CATEGORIES:
1 piece ES PROLINE
Parameter | Unit | A1-A3 | A4 | A5 | B6 | C1 | C2 | C3 | C4 | D |
---|---|---|---|---|---|---|---|---|---|---|
HWD | [kg] | 9.58E-6 | 9.76E-7 | 2.27E-8 | 2.90E-6 | 3.05E-11 | 1.27E-7 | 1.55E-8 | 0.00E+0 | -1.17E-7 |
NHWD | [kg] | 7.85E+0 | 4.77E-3 | 1.37E-1 | 4.96E+0 | 5.23E-5 | 4.83E-4 | 1.04E+0 | 0.00E+0 | -4.87E+0 |
RWD | [kg] | 4.74E-2 | 4.29E-5 | 2.35E-4 | 1.06E+0 | 1.12E-5 | 4.93E-6 | 1.45E-4 | 0.00E+0 | -2.41E-2 |
CRU | [kg] | 0.00E+0 | 0.00E+0 | 0.00E+0 | 0.00E+0 | 0.00E+0 | 0.00E+0 | 0.00E+0 | 0.00E+0 | 0.00E+0 |
MFR | [kg] | 2.89E+0 | 0.00E+0 | 0.00E+0 | 0.00E+0 | 0.00E+0 | 0.00E+0 | 2.12E+1 | 0.00E+0 | 0.00E+0 |
MER | [kg] | 0.00E+0 | 0.00E+0 | 0.00E+0 | 0.00E+0 | 0.00E+0 | 0.00E+0 | 3.43E+0 | 0.00E+0 | 0.00E+0 |
EEE | [MJ] | 0.00E+0 | 0.00E+0 | 6.57E+0 | 0.00E+0 | 0.00E+0 | 0.00E+0 | 1.29E+1 | 0.00E+0 | 0.00E+0 |
EET | [MJ] | 0.00E+0 | 0.00E+0 | 1.19E+1 | 0.00E+0 | 0.00E+0 | 0.00E+0 | 2.76E+1 | 0.00E+0 | 0.00E+0 |
Caption: HWD = Hazardous waste disposed; NHWD = Non-hazardous waste disposed; RWD = Radioactive waste disposed; CRU = Components for re-use; MFR = Materials for recycling; MER = Materials for energy recovery; EEE = Exported electrical energy; EEE = Exported thermal energy
6. LCA: Interpretation
The CML characterization factors were used for the evaluation. The results of the CML categories refer to the potential environmental impacts over a period of 100 years.
The main impacts lie in the modules A1-A3 and B6. The impacts in module B6 are due to the electricity mix used for modelling the electricity consumption over a period of 15 years. In the following, the main influences on the modules A1-A3 for the indicators will be explained.
The indicators ozone depletion potential (ODP), eutrophication potential (EP) and abiotic depletion potential for non-fossil resources (ADPE) in module A1-A3 are more than 90% dominated by the electronic components. The other CML indicators are also dominated by the electronic components. However, the aluminium also has a significant impact. The aluminium contributes 28% to global warming potential (GWP), 23% to abiotic depletion potential for fossil resources (ADPF), 14% to formation potential of tropospheric ozone photochemical oxidants (POCP) and 12% to acidification potential (AP).
7. Requisite evidence
8. References
Standards
- EN 15804: EN 15804:2012-04+A1 2013, Sustainability of construction works -- Environmental Product Declarations -- Core rules for the product category of construction products.
- EN 16005: DIN EN 16005:2013-01 and Amendment 2015-10, Power operated pedestrian doorsets - Safety in use - Requirements and test methods.
- EN 60335-2-103: DIN EN 60335-2-103:2016-05, Household and similar electrical appliances - Safety - Part 2-103: Particular requirements for drives for gates, doors and windows.
- EN 61000-3-2: DIN EN 61000-3-2:2015-03, Electromagnetic compatibility (EMC) - Part 3-2: Limits - Limits for harmonic current emissions (equipment input current ≤ 16 A per phase).
- EN 61000-3-3: DIN EN 61000-3-3:2014-03, Electromagnetic compatibility (EMC) - Part 3-3: Limits - Limitation of voltage changes, voltage fluctuations and flicker in public low-voltage supply systems, for equipment with rated current ≤ 16 A per phase and not subject to conditional connection.
- EN 61000-6-2: DIN EN 61000-6-2:2005 + Amendment:2011. Electromagnetic compatibility (EMC) - Part 6-2: Generic standards - Immunity standard for industrial environments.
- EN 61000-6-3: DIN EN 61000-6-3:2007 + A1:2011, Electromagnetic compatibility (EMC) - Part 6-3: Generic standards - Emission standard for residential, commercial and light-industrial environments.
- IEC 63000: DIN EN IEC 63000:2019-05, Technical documentation for the assessment of electrical and electronic products with respect to the restriction of hazardous substances.
- ISO 9001: DIN EN ISO 9001:2015-11, Quality management systems - Requirements.
- ISO 12100: DIN EN ISO 12100:2011-03, Safety of machinery - General principles for design - Risk assessment and risk reduction.
- ISO 14001: ISO 14001:2015-09, Environmental management systems - Requirements with guidance for use.
- ISO 14025: DIN EN ISO 14025:2011-10, Environmental labels and declarations - Type III environmental declarations - Principles and procedures.
- ISO 13849-1: DIN EN ISO 13849-1:2016-06, Safety of machinery - Safety-related parts of control systems - Part 1: General principles for design.
- ISO 13849-2: DIN EN ISO 13849-2:2013-02, Safety of machinery - Safety-related parts of control systems - Part 2: Validation.
- OHSAS 18001: Occupational health and safety – Management systems - Requirements
Further references
- 2011/65/EU ROHS3 Directive: Directive 2011/65/EU of the European Parliament and of the Council of 8 June 2011 on the restriction of the use of certain hazardous substances in electrical and electronic equipment.
- 2014/30/EU Electromagnetic Compatibility Directive: Directive 2014/30/EU of the European Parliament and of the Council of 26 February 2014 on the harmonisation of the laws of the Member States relating to electromagnetic compatibility (recast).
- Candidate List: Candidate List of substances of very high concern for Authorisation (published in accordance with Article 59(10) of the REACH Regulation).
- CML: Institute of Environmental Sciences Leiden University.
- Ecoinvent Version 2.2: Database for life cycle assessment (life cycle inventory data), Version 2.2, 2010.
- Ecoinvent Version 3.6: Database for life cycle assessment (life cycle inventory data), Version 3.6, 2019.
- EWC: European Waste Catalogue (EWC). Commission Decision on the European List of Waste (COM 2000/532/EC).
- GaBi 9.5: Life cycle engineering (GaBi) software and database. LBP, University of Stuttgart and thinkstep AG, Documentation of GaBi 9.5 data sets http://documentation.gabisoftware.com/, 2020.
- IBU 2016: Institut Bauen und Umwelt e.V.: General Programme Instructions for the Preparation of EPDs at the Institut Bauen und Umwelt e.V. Version 1., Berlin: Institut Bauen und Umwelt e.V., 2016. www.ibu-epd.com.
- IP: Ingress Protection Rating. DIN EN 60529; VDE 04701: 201409: Degrees of protection provided by enclosures (IP Code) (IEC 60529:1989 + A1:1999 + A2:2013); German version EN 60529:1991 + A1:2000 + A2:2013.
- Machinery Directive 2006/42/EC: Directive 2006/42/EC of the European Parliament and of the Council of 17 May 2006 on machinery, and amending Directive 95/16/EC (recast).
- Ordinance on Biocide Products No. 528/2012: Regulation (EU) No 528/2012 of the European Parliament and of the Council of 22 May 2012 concerning the making available on the market and use of biocidal products.
- Product Category Rules Part A: Calculation Rules for the Life Cycle Assessment and Requirements on the Project Report. Version 1.8 (04.07.2019).
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Contact Information
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Author of the Life Cycle Assessment brands & values GmbH Altenwall 14 28195 Bremen Germany | Tel: +49 421 70 90 84 33 Fax: +49 421 70 90 84 35 Mail: info@brandsandvalues.com Web: www.brandsandvalues.com |
Owner of the Declaration dormakaba International Holding GmbH DORMA Platz 1 58256 Ennepetal Germany | Tel: +49 2333 793-0 Fax: +49 2333 793-4950 Mail: info.de@dormakaba.com Web: www.dormakaba.com |