Lindab DSU Dampers In Galvanized Steel Instruction Manual
- June 1, 2024
- Lindab
Table of Contents
- Lindab DSU Dampers In Galvanized Steel
- Product Usage Instructions
- GENERAL INFORMATION
- MANUFACTURER
- PRODUCT
- PRODUCT DESCRIPTION
- PRODUCT LIFE-CYCLE
- TRANSPORT AND INSTALLATION (A4-A5)
- MANUFACTURING PROCESS
- LIFE-CYCLE ASSESSMENT
- ENVIRONMENTAL IMPACT DATA
- References
- Read User Manual Online (PDF format)
- Download This Manual (PDF format)
Lindab DSU Dampers In Galvanized Steel
Specifications:
- Product Name: Lindab Manual Dampers in galvanized steel
- Product Reference: VP-013
- Place of Production: VP-008
- Declared Unit: Unit
- Declared Unit Mass: Not specified
- GWP-fossil, A1-A3: Information available on page 7
- GWP-total, A1-A3: Information available on page 7
- Total Energy Use, A1-A3: Information available on page 7
- Total Water Use, A1-A3: Information available on page 7
Product Usage Instructions
Environmental Product Declaration:
The Lindab Manual Dampers in galvanized steel have an Environmental Product
Declaration (EPD) in accordance with EN 15804+A2 & ISO 14025 / ISO 21930.
Manufacturing and Packaging:
The steel raw material is received by Lindab Group’s own steel service centre,
Lindab Steel AB. After a quality control process,the most suitable coil is
selected for manufacturing orders to minimize scrap. The coil is then
processed into correct dimensions through slitting, re-coiling, or cutting to
length.
Substances and Reach:
The product does not contain any REACH SVHC substances in amounts greater than
0.1% (1000 ppm). More detailed information about the product’s material
content can be found in the Building Product Declaration available online.
Geographical Scope:
The product is intended for use in Europe.
Product Life-Cycle:
The EPD covers various life-cycle stages from raw materials sourcing to end-
of-life considerations. Modules not declared are marked as MND, and modules
not relevant are marked as MNR.
FAQ:
Q: Where can I find more detailed environmental data about the product?
A: More detailed information regarding GWP-fossil, GWP-total,total energy
use, and total water use for A1-A3 stages can be found on page 7 of the
document.
ENVIRONMENTAL PRODUCT DECLARATION
IN ACCORDANCE WITH EN 15804+A2 & ISO 14025 / ISO 21930
Lindab Safe Manual Dampers – DRU, DRH1U, DRHU, DRPU, DSU, DSHU, DTU, DTH1U,
DTH2U, DTHU, DTMU
Lindab Ventilation AB
EPD Registration number: HUB-1221
Version: 1.0
Publication date: 22.03.2024
Valid until: 22.03.2029
Revision date: 22.03.2024
GENERAL INFORMATION
MANUFACTURER
| Manufacturer | Lindab Ventilation AB |
|---|---|
| Address | Stålhögavägen 117, 269 82 Båstad, Sweden |
| Contact details | lindab@lindab.com |
| Website | https://www.lindab.com |
EPD STANDARDS, SCOPE AND VERIFICATION
| Program operator | EPD Hub, hub@epdhub.com |
|---|---|
| Reference standard | EN 15804+A2:2019 and ISO 14025 |
| PCR | EPD Hub Core PCR version 1.0, 1 Feb 2022 |
| Sector | Construction product |
| Category of EPD | Third party verified EPD |
| Scope of the EPD | Cradle to gate with options, A4-A5, and modules C1-C4, D |
| EPD author | Kerstin Bergström |
EPD verification
| Independent verification of this EPD and data, according to ISO 14025:
£ Internal certification þ External verification
EPD verifier| Magaly Gonzalezvazquez, as an authorized verifier acting for EPD Hub Limited
The manufacturer has the sole ownership, liability, and responsibility for the EPD. EPDs within the same product category but from different programs may not be comparable. EPDs of construction products may not be comparable if they do not comply with EN 15804 and if they are not compared in a building context.
PRODUCT
| Product name | Lindab Manual Dampers in galvanized steel |
|---|---|
| Additional labels | |
| Product reference | DRU, DRH1U, DRHU, DRPU, DSU, DSHU, DTU, DTH1U, DTH2U, DTHU, |
DTMU
Place of production
| Lindab s.r.o., Na Hurce 1081/6, Prague, Czech Republic
Lindab Ventilation AB, Stålhögavägen 115, Grevie (Båstad)
Period for data| Calendar year 2022
Averaging in EPD| Multiple factories
Variation in GWP-fossil for A1-A3| <10%
More information on page 7.
ENVIRONMENTAL DATA SUMMARY
| Declared unit | 1kg of manual dampers in galvanized steel |
|---|---|
| Declared unit mass | 1 kg |
| GWP-fossil, A1-A3 (kgCO2e) | 4,07 |
| GWP-total, A1-A3 (kgCO2e) | 3,64 |
| Secondary material, inputs (%) | 8,93 |
| Secondary material, outputs (%) | 99,0 |
| Total energy use, A1-A3 (kWh) | 14,9 |
| Total water use, A1-A3 (m3e) | 0,02 |
MANUFACTURER
ABOUT LINDAB
Lindab is a leading ventilation company in Europe, offering solutions for
energy-efficient ventilation and a healthy indoor climate. The products are
characterised by high quality, ease of installation and environmental
thinking. In northern Europe, Lindab also offers an extensive range of roof,
wall and rainwater systems.
FOR A BETTER CLIMATE
We want to create a better climate. Most of us spend a majority of our time
indoors. The air we breathe, in our homes, at our workplaces and at school,
affects our well-being. Since air is not visible, we do not always think about
it. However, the indoor climate is crucial for how we feel, for our energy
levels and whether we stay healthy. Lindab wants to contribute to the
architecture and indoor climate of tomorrow. We also want a better climate for
our planet. That is why we develop energy-efficient solutions for healthy
indoor environments.
OUR VISION
We want to be the leading player in the area in which we are strongest –
ventilation in Europe. We focus on air distribution and air diffusion. Since
we offer high-quality products, we focus on Europe where demand for good
ventilation is high, and we can offer superior availability. We specialise in
those parts of the ventilation system where we are the strongest. We adapt our
offering to the local market, with our core ventilation offering as the clear
common denominator in all markets.
THE IMPORTANCE OF VENTILATION
About 90 percent of the global population breathes poor air every day. A
common misconception is that outdoor air is more polluted due to emissions,
smog, and harmful chemicals. In fact, indoor air in homes, schools, offices,
and factories can be as much as five times more polluted. People nonetheless
spend most of their life indoors. The most common causes of indoor air
pollution are mold, chemicals in, for example, furniture and building
materials, dust, radon, and cigarette smoke but, above all, airborne particles
from combustion and industrial processes, which are so small they can enter
the human bloodstream via the respiratory system. Today, air pollution is a
risk factor in several of the world’s most common causes of death, including
heart disease, pneumonia, stroke, diabetes, and lung cancer. Ventilation is an
efficient and convenient method to remove those indoor air pollutants.
SUSTAINABILITY PLAN
For us, sustainability is a way of thinking and working. This affects how
we work with Lindab’s strategy in all areas. Everything from the purchases we
make, to the deliveries and the service we offer our customers. Lindab has
three long-term, non-financial targets for the business, one that focuses on
increasing our attractiveness as an employer, one for reducing our own carbon
dioxide emissions, and one for a better working environment. Read more about
Lindab Groups sustainability work and non-financial targets on
www.lindabgroup.com.
STEEL – A SUSTAINABLE MATERIAL
Steel provides products with a long service life. Steel has many advantages
over other materials – it has a very long service life, is non-combustible and
meets hygiene requirements. Steel is a fully recyclable material and scrap
steel has a strong market position: steel recovered from structures and end
products at the end of their lifecycle is efficiently recycled and re-used. We
prioritise cooperation with steel suppliers driving development towards
fossil-free steel and whose carbon dioxide intensity values are good. The
steel we use must be free of particularly hazardous substances.
The use of steel in Lindab’s products is what contributes most to Lindab’s CO2
emissions. The transition to decarbonised steel is Lindab’s most significant
individual action in terms of its effect on the environment. Through our
collaboration with SSAB and H2 Green Steel, we will also be among the first in
Europe to have access to recycled, near-zero and fossil free steel in 2026.
PRODUCT
PRODUCT DESCRIPTION
The main material of manual dampers is galvanized steel (Z275). Dampers are
used in ventilation duct systems to control the airflow.
The manual dampers are produced according to EN1506, EN12237 & EN1751 and are
installed using screws or rivets.
The Lindab manual dampers have a blade in the airstream to create a pressure
drop and are normally equipped with a factory installed double-lipped EPDM
rubber gasket at the joints for optimal tightness (Eurovent certified for
tightness class D), performance and easy installation.
Manual dampers can vary in:
- Size
- With or without a shelf to be prepared for a motor
- Shut-off functionality (blade with steel and EPDM rubber) or
- Regulation functionality (blade only with steel)
Further information can be found at www.lindab.com/air-distribution/dampers-
and-measure
units.
For product specific GWP calculations see additional document [EPD values
Galvanized steel (file type: xlsx] which is presented for each product on
www.lindab.com.
PRODUCT RAW MATERIAL MAIN COMPOSITION VP
| Raw material category | Amount, mass- % | Material origin |
|---|---|---|
| Metals | 96 | EU/Asia |
| Minerals | – | |
| Fossil materials | 4 | EU |
| Bio-based materials | – |
BIOGENIC CARBON CONTENT VP028-C
Product’s biogenic carbon content at the factory gate
| Biogenic carbon content in product, kg C | 0 |
|---|---|
| Biogenic carbon content in packaging, kg C | 0,048 |
FUNCTIONAL UNIT AND SERVICE LIFE
| Declared unit | 1kg of manual dampers in galvanized steel |
|---|---|
| Mass per declared unit | 1kg |
| Functional unit | – |
| Reference service life | >50 years |
The reference service life of the product is highly dependent on the conditions of use, average lifespan under normal conditions is minimum 50 years. This is an estimated value based on experience and scientific facts about steel.
SUBSTANCES, REACH – VERY HIGH CONCERN VP-027-C
The product does not contain any REACH SVHC substances in amounts greater than 0,1 % (1000 ppm). More detailed information about the products material content can be found in the Building Product Declaration available online.
GEOGRAPHICAL SCOPE
Europe
PRODUCT LIFE-CYCLE
SYSTEM BOUNDARY
This EPD covers the life-cycle modules listed in the following table.
Product stage| Assembly stage| Use stage| End of life
stage| Beyond the system boundaries
---|---|---|---|---
A1| A2| A3| A4| A5| B1| B2| B3|
B4| B5| B6| B7| C1| C2| C3| C4| D
x| x| x| x| x| MND| MND| MND|
MND| MND| MND| MND| x| x| x| x| x
Raw materials| Transport| Manufacturing|
Transport
|
Assembly
|
Use
|
Maintenance
|
Repair
|
Replacement
|
Refurbishment
| Operational energy
use
| Operational water
use
| Deconstruction
/Demolition
| Transport| Waste processing| Disposal| Reuse| Recovery| Recycling
Modules not declared = MND. Modules not relevant = MNR.
MANUFACTURING AND PACKAGING (A1-A3) VP-018
The environmental impacts considered for the product stage cover the
manufacturing of raw materials used in the production as well as packaging
materials and other ancillary materials. Also, fuels used by machines, and
handling of waste generated in the production processes at the manufacturing
facilities are included in this stage. The study also considers the material
losses occurring during the manufacturing processes as well as losses during
electricity transmission.
The steel raw material is received by Lindab Group’s own steel service centre, Lindab Steel AB. After a quality control the most suitable coil is selected for the manufacturing orders, to minimize scrap. The coil is slitted into correct dimensions, re-coiled or cut to length.
The damper is produced by galvanized steel from coil, pressed, rounded and welded to a body and assembled with shaft, bearing, blade and lock washer. The finished product is packed in a, for the specific size, appropriate manner, e.g. wooden pallet and cardboard box.
The power required to produce the manual dampers is mainly sourced from electricity grid mix in Czeck Republic, but also wind power in Sweden. All production waste is sent to a recycling company.
TRANSPORT AND INSTALLATION (A4-A5)
Transportation impacts occurred from final products delivery to construction site (A4) cover fuel direct exhaust emissions, environmental impacts of fuel production, as well as related infrastructure emissions. Installation spills and handling of packaging material is considered. Material loss during installation is estimated to be zero. The transportation distance is based on the market share per country. The distance for transportation of installation waste to waste management facility is assumed to be 50 km as per an estimation of the locations of warehouses. Transport from distribution centre to customer is set to 300 km.
Transport from production place to user (A4)
Manufacturing site| Total dist. (km)| Transportation
method
---|---|---
SWE| 991+4| Lorry + ferry
CZ| 929+4| Lorry + ferry
PRODUCT USE AND MAINTENANCE (B1-B7) VP-043-C
This EPD does not cover the use phase. These life cycle stages are dependent
on how the product is used and should be developed and included as part of a
holistic assessment of specific construction works.
PRODUCT END OF LIFE (C1-C4, D) VP-049-C
Energy (0,1kWh) for deconstruction is included in C1, and activities
related to steel recycling is included in C3. A recycling rate of 95%
(according to World Steel Association, 2017) and landfill rate of 5% has been
assumed for the product. That is to be seen as the proportion of the material
in the product that will be recycled in a subsequent system. External scrap in
the raw material is also deducted and accounts for 20%. Hence the net flow to
be credited in module D is 76%.
The dampers are demounted by destroying the lock washer and disassemble all
the other parts.
See below tables for scenarios used in Modules C and D, based on Lindab Sustainability reporting scenarios.
Transport to waste processing scenario (A5, C2)
| Type | Distance |
|---|---|
| Lorry | 50 km |
End of Life Scenarios (A5, C3, C4, D)
| % | |
|---|---|
| Metal to recycling | 95 |
| Metal to landfill | 5 |
| Paper to recycling | 90 |
| Paper to landfill | 10 |
| Plastic and rubber to recycling | 30 |
| Plastic and rubber to incineration | 70 |
| Wood to incineration | 100 |
End of life scenarios are based on Lindab sustainability reporting 2022.
MANUFACTURING PROCESS
LIFE-CYCLE ASSESSMENT
CUT-OFF CRITERIA VP-020
The study does not exclude any modules or processes which are stated mandatory
in the reference standard and the applied PCR. The study does not exclude any
hazardous materials or substances. The study includes all major raw material
and energy consumption. All inputs and outputs of the unit processes, for
which data is available for, are included in the calculation.
There is no neglected unit process more than 1% of total mass or energy flows.
The module-specific total neglected input and output flows also do not exceed
5% of energy usage or mass.
ALLOCATION, ESTIMATES AND ASSUMPTIONS VP-050-C
Allocation is required if some material, energy, and waste data cannot be
measured separately for the product under investigation. All allocations are
done as per the reference standards and the applied PCR. In this study,
allocation has been done in the following ways:
| Data type | Allocation |
|---|---|
| Raw materials | No allocation |
| Packaging materials | No allocation |
| Ancillary materials | Allocated by mass or volume |
| Manufacturing energy and waste | Weighted average for the two manufacturing |
sites
AVERAGES AND VARIABILITY
| Type of average | Multiple production sites |
|---|---|
| Averaging method | Representative product |
| Variation in GWP-fossil for A1-A3 | <10% |
This EPD is represented by the article DSU 100. DSU 100 is the high runner and
represents Manual dampers in this EPD well. This EPD represents an average of
two production sites Grevie, Sweden and Karlovarska, Czech Republic.
Impacts on GWP fossil in A1-A3 modules, because of variance energy sources and
amount of waste and scrap between each of the sites, is less than +/-10%.
Production process, transportation, installation, demolition, and waste
treatment are the same for all articles. Result is weighted by the annual
product sales from each site.
LCA SOFTWARE AND BIBLIOGRAPHY
This EPD has been created using One Click LCA EPD Generator. The LCA and EPD
have been prepared according to the reference standards and ISO 14040/14044.
Data from available supplier EPDs, Ecoinvent 3.8 and One Click LCA databases
were used as sources of environmental data.
ENVIRONMENTAL IMPACT DATA
CORE ENVIRONMENTAL IMPACT INDICATORS – EN 15804+A2, PEF
IMPACT CATEGORY| UNIT| A1| A2| A3| A1-A3| A4| A5| B1| B2| B3| B4| B5| B6| B7|
C1| C2| C3| C4| D
---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---
GWP – TOTAL| kg CO2e| 3,51E+00| 9,45E‐02| 3,99E‐02| 3,64E+00| 1,01E‐01|
4,27E‐01| MND| MND| MND| MND| MND| MND| MND| 4,38E‐02| 4,88E‐03| 1,35E‐01|
8,80E‐04| ‐
1,67E+00
GWP – FOSSIL| kg CO2e| 3,52E+00| 9,44E‐02| 4,61E‐01| 4,07E+00| 1,01E‐01| 2,22E‐03| MND| MND| MND| MND| MND| MND| MND| 4,37E‐02| 4,88E‐03| 1,23E‐01| 2,53E‐04| ‐
1,67E+00
GWP – BIOGENIC| kg CO2e| ‐1,34E‐02| 5,11E‐07| ‐4,22E‐01| ‐4,35E‐01| 0,00E+00|
4,25E‐01| MND| MND| MND| MND| MND| MND| MND| 0,00E+00| 0,00E+00| 1,17E‐02|
6,27E‐04| 0,00E+00
GWP – LULUC| kg CO2e| 9,83E‐04| 3,48E‐05| 8,72E‐04| 1,89E‐03| 3,63E‐05|
2,19E‐06| MND| MND| MND| MND| MND| MND| MND| 6,43E‐05| 1,80E‐06| 2,83E‐05|
2,39E‐07| ‐9,95E‐04
OZONE DEPLETION POT.| kg CFC-11e| 5,29E‐08| 2,18E‐08| 1,67E‐08| 9,14E‐08|
2,40E‐08| 1,83E‐10| MND| MND| MND| MND| MND| MND| MND| 2,10E‐09| 1,12E‐09|
2,82E‐09| 1,02E‐10| ‐7,57E‐08
ACIDIFICATION POTENTIAL| mol H+e| 1,02E‐02| 3,99E‐04| 2,15E‐03| 1,27E‐02|
4,35E‐04| 9,14E‐06| MND| MND| MND| MND| MND| MND| MND| 2,36E‐04| 2,07E‐05|
2,82E‐04| 2,38E‐06| ‐7,27E‐03
EP-FRESHWATER| kg Pe| 2,09E‐05| 7,60E‐07| 7,12E‐05| 9,28E‐05| 6,89E‐07|
9,54E‐08| MND| MND| MND| MND| MND| MND| MND| 5,43E‐06| 3,99E‐08| 1,14E‐06|
2,65E‐09| ‐7,74E‐05
EP-MARINE| kg Ne| 2,25E‐03| 1,19E‐04| 4,08E‐04| 2,78E‐03| 1,31E‐04| 2,13E‐06|
MND| MND| MND| MND| MND| MND| MND| 3,01E‐05| 6,14E‐06| 6,28E‐05| 8,23E‐07|
‐1,49E‐03
EP-TERRESTRIAL| mol Ne| 2,37E‐02| 1,31E‐03| 4,33E‐03| 2,93E‐02| 1,44E‐03|
2,12E‐05| MND| MND| MND| MND| MND| MND| MND| 3,41E‐04| 6,77E‐05| 7,19E‐04|
9,05E‐06| ‐1,74E‐02
POCP (“SMOG”)| kg NMVOCe| 7,56E‐03| 4,19E‐04| 1,29E‐03| 9,27E‐03| 4,60E‐04|
6,39E‐06| MND| MND| MND| MND| MND| MND| MND| 9,38E‐05| 2,17E‐05| 1,96E‐04|
2,63E‐06| ‐7,57E‐03
ADP-MINERALS & METALS| kg Sbe| 1,97E‐04| 2,24E‐07| 1,44E‐06| 1,98E‐04|
2,35E‐07| 1,80E‐08| MND| MND| MND| MND| MND| MND| MND| 9,58E‐08| 1,15E‐08|
2,82E‐06| 5,81E‐10| ‐2,50E‐05
ADP-FOSSIL RESOURCE| MJ| 3,91E+01| 1,42E+00| 6,91E+00| 4,74E+01| 1,54E+00|
2,72E‐02| MND| MND| MND| MND| MND| MND| MND| 8,76E‐01| 7,33E‐02| 2,99E‐01|
6,93E‐03| ‐
1,69E+01
WATER USE| m3e depr.| 1,13E+00| 6,38E‐03| 3,64E‐01| 1,51E+00| 7,08E‐03| 5,89E‐04| MND| MND| MND| MND| MND| MND| MND| 1,93E‐02| 3,28E‐04| 8,44E‐03| 2,20E‐05| ‐4,78E‐01
ENVIRONMENTAL IMPACTS – GWP-GHG – THE INTERNATIONAL EPD SYSTEM
IMPACT CATEGORY
| ****
UNIT
| ****
A1
| ****
A2
| ****
A3
| ****
A1-A3
| ****
A4
| ****
A5
| ****
B1
| ****
B2
| ****
B3
| ****
B4
| ****
B5
| ****
B6
| ****
B7
| ****
C1
| ****
C2
| ****
C3
| ****
C4
| ****
D
---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---
GWP-GHG*)| kg CO2e| 3,52E+00| 9,44E‐02| 4,61E‐01| 4,07E+00| 1,01E‐01|
2,22E‐03| MND| MND| MND| MND| MND| MND| MND| 4,37E‐02| 4,88E‐03| 1,23E‐01|
2,53E‐04| ‐1,67E+00
This indicator includes all greenhouse gases excluding biogenic carbon dioxide uptake and emissions and biogenic carbon stored in the product as defined by IPCC AR 5 (IPCC 2013). In addition, the characterisation factors for the flows – CH4 fossil, CH4 biogenic and Dinitrogen monoxide – were updated in line with the guidance of IES PCR 1.2.5 Annex 1. This indicator is identical to the GWP- total of EN 15804:2012+A2:2019 except that the characterization factor for biogenic CO2 is set to zero.
USE OF NATURAL RESOURCES
IMPACT CATEGORY| UNIT| A1| A2| A3| A1-A3| A4| A5| B1| B2| B3| B4| B5| B6| B7|
C1| C2| C3| C4| D
---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---
Renew. PER as energy8)| MJ| 3,17E+00| 1,63E‐02| 2,63E+00| 5,82E+00| 1,98E‐02|
3,09E‐03| MND| MND| MND| MND| MND| MND| MND| 1,27E‐01| 8,27E‐04| 5,09E‐02|
6,02E‐05| ‐
3,10E+00
Renew. PER as material| MJ| 2,12E‐01| 0,00E+00| 3,79E+00| 4,00E+00| 0,00E+00|
‐3,83E+00| MND| MND| MND| MND| MND| MND| MND| 0,00E+00| 0,00E+00| ‐1,67E‐01|
‐8,79E‐03| 0,00E+00
Total use of renew. PER| MJ| 3,38E+00| 1,63E‐02| 6,42E+00| 9,82E+00| 1,98E‐02|
‐3,83E+00| MND| MND| MND| MND| MND| MND| MND| 1,27E‐01| 8,27E‐04| ‐1,16E‐01|
‐8,73E‐03| ‐
3,10E+00
Non-re. PER as energy| MJ| 3,95E+01| 1,42E+00| 6,70E+00| 4,76E+01| 1,54E+00| 2,71E‐02| MND| MND| MND| MND| MND| MND| MND| 8,77E‐01| 7,33E‐02| 2,99E‐01| 6,93E‐03| ‐
1,69E+01
Non-re. PER as material| MJ| 9,69E‐01| 0,00E+00| 2,05E‐01| 1,17E+00| 0,00E+00|
‐2,08E‐01| MND| MND| MND| MND| MND| MND| MND| 0,00E+00| 0,00E+00| ‐9,67E‐01|
‐4,95E‐04| 0,00E+00
Total use of non-re. PER| MJ| 4,05E+01| 1,42E+00| 6,90E+00| 4,88E+01|
1,54E+00| ‐1,80E‐01| MND| MND| MND| MND| MND| MND| MND| 8,77E‐01| 7,33E‐02|
‐6,67E‐01| 6,44E‐03| ‐
1,69E+01
Secondary materials| kg| 8,93E‐02| 3,96E‐04| 3,11E‐02| 1,21E‐01| 4,34E‐04|
2,92E‐05| MND| MND| MND| MND| MND| MND| MND| 6,63E‐05| 2,04E‐05| 3,30E‐04|
1,46E‐06| ‐1,73E‐01
Renew. secondary fuels| MJ| 9,68E‐04| 3,97E‐06| 1,06E‐01| 1,07E‐01| 3,82E‐06|
1,26E‐07| MND| MND| MND| MND| MND| MND| MND| 3,73E‐07| 2,06E‐07| 1,69E‐05|
3,80E‐08| ‐3,66E‐04
Non-ren. secondary fuels| MJ| 7,22E‐22| 0,00E+00| 0,00E+00| 7,22E‐22|
0,00E+00| 0,00E+00| MND| MND| MND| MND| MND| MND| MND| 0,00E+00| 0,00E+00|
0,00E+00| 0,00E+00| 0,00E+00
Use of net fresh water| m3| 9,96E‐03| 1,84E‐04| 1,04E‐02| 2,05E‐02| 2,03E‐04|
1,73E‐05| MND| MND| MND| MND| MND| MND| MND| 6,78E‐04| 9,49E‐06| 2,99E‐04|
7,59E‐06| ‐1,04E‐02
END OF LIFE – WASTE
IMPACT CATEGORY| UNIT| A1| A2| A3| A1-A3| A4| A5| B1| B2| B3| B4| B5| B6| B7|
C1| C2| C3| C4| D
---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---
Hazardous waste| kg| 3,28E‐01| 1,85E‐03| 1,82E‐02| 3,48E‐01| 1,66E‐03|
1,68E‐04| MND| MND| MND| MND| MND| MND| MND| 3,13E‐03| 9,72E‐05| 2,57E‐03|
0,00E+00| ‐7,22E‐01
Non-hazardous waste| kg| 9,46E‐01| 3,05E‐02| 3,14E+00| 4,11E+00| 2,87E‐02|
5,14E‐03| MND| MND| MND| MND| MND| MND| MND| 2,49E‐01| 1,60E‐03| 9,55E‐02|
4,80E‐02| ‐
3,14E+00
Radioactive waste| kg| 5,53E‐04| 9,53E‐06| 3,53E‐05| 5,98E‐04| 1,06E‐05| 1,74E‐07| MND| MND| MND| MND| MND| MND| MND| 6,00E‐06| 4,90E‐07| 1,68E‐06| 0,00E+00| ‐3,32E‐05
END OF LIFE – OUTPUT FLOWS
IMPACT CATEGORY| UNIT| A1| A2| A3| A1-A3| A4| A5| B1| B2| B3| B4| B5| B6| B7|
C1| C2| C3| C4| D
---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---
Components for re-use| kg| 4,87E‐06| 0,00E+00| 0,00E+00| 4,87E‐06| 0,00E+00|
0,00E+00| MND| MND| MND| MND| MND| MND| MND| 0,00E+00| 0,00E+00| 0,00E+00|
0,00E+00| 0,00E+00
Materials for recycling| kg| 2,95E‐02| 0,00E+00| 1,96E‐01| 2,25E‐01| 0,00E+00|
4,30E‐02| MND| MND| MND| MND| MND| MND| MND| 0,00E+00| 0,00E+00| 9,65E‐01|
0,00E+00| 0,00E+00
Materials for energy rec| kg| 0,00E+00| 0,00E+00| 0,00E+00| 0,00E+00|
0,00E+00| 5,10E‐02| MND| MND| MND| MND| MND| MND| MND| 0,00E+00| 0,00E+00|
2,49E‐02| 0,00E+00| 0,00E+00
Exported energy| MJ| 0,00E+00| 0,00E+00| 0,00E+00| 0,00E+00| 0,00E+00|
2,30E+00| MND| MND| MND| MND| MND| MND| MND| 0,00E+00| 0,00E+00| 4,87E‐01|
0,00E+00| 0,00E+00
ENVIRONMENTAL IMPACTS – EN 15804+A1, CML / ISO 21930
IMPACT CATEGORY| UNIT| A1| A2| A3| A1-A3| A4| A5| B1| B2| B3| B4| B5| B6| B7|
C1| C2| C3| C4| D
---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---
Global Warming Pot.| kg CO2e| 3,47E+00| 9,35E‐02| 4,58E‐01| 4,02E+00|
9,96E‐02| 2,55E‐03| MND| MND| MND| MND| MND| MND| MND| 4,33E‐02| 4,83E‐03|
1,23E‐01| 2,48E‐04| ‐1,60E+00
Ozone depletion Pot.| kg CFC-11e| 4,30E‐08| 1,73E‐08| 1,42E‐08| 7,45E‐08|
1,90E‐08| 1,50E‐10| MND| MND| MND| MND| MND| MND| MND| 1,82E‐09| 8,89E‐10|
2,30E‐09| 8,09E‐11| ‐7,73E‐08
Acidification| kg SO2e| 9,06E‐03| 3,10E‐04| 1,76E‐03| 1,11E‐02| 3,37E‐04|
7,37E‐06| MND| MND| MND| MND| MND| MND| MND| 2,01E‐04| 1,60E‐05| 2,26E‐04|
1,80E‐06| ‐5,84E‐03
Eutrophication| ****
3
kg PO4 e
| 1,59E‐03| 7,05E‐05| 2,30E‐03| 3,96E‐03| 7,39E‐05| 7,12E‐06| MND| MND| MND|
MND| MND| MND| MND| 1,88E‐04| 3,66E‐06| 1,06E‐04| 3,87E‐07| ‐3,23E‐03
POCP (“smog”)| kg C2H4e| 8,52E‐04| 1,21E‐05| 9,66E‐05| 9,60E‐04| 1,31E‐05|
5,91E‐07| MND| MND| MND| MND| MND| MND| MND| 8,20E‐06| 6,27E‐07| 8,66E‐06|
7,53E‐08| ‐8,05E‐04
ADP-elements| kg Sbe| 1,96E‐04| 2,17E‐07| 1,43E‐06| 1,98E‐04| 2,29E‐07|
1,79E‐08| MND| MND| MND| MND| MND| MND| MND| 9,55E‐08| 1,11E‐08| 2,82E‐06|
5,72E‐10| ‐2,49E‐05
ADP-fossil| MJ| 3,91E+01| 1,42E+00| 6,91E+00| 4,74E+01| 1,54E+00| 2,71E‐02|
MND| MND| MND| MND| MND| MND| MND| 8,76E‐01| 7,33E‐02| 2,99E‐01| 6,93E‐03|
‐1,69E+01
VERIFICATION STATEMENT
VERIFICATION PROCESS FOR THIS EPD
This EPD has been verified in accordance with ISO 14025 by an independent,
third-party verifier by reviewing results, documents and compliancy with
reference standard, ISO 14025 and ISO 14040/14044, following the process and
checklists of the program operator for:
- This Environmental Product Declaration
- The Life-Cycle Assessment used in this EPD
- The digital background data for this EPD
Why does verification transparency matter? Read more online
This EPD has been generated by One Click LCA EPD generator, which has been
verified and approved by the EPD Hub.
THIRD-PARTY VERIFICATION STATEMENT
I hereby confirm that, following detailed examination, I have not established
any relevant deviations by the studied Environmental Product Declaration
(EPD), its LCA and project report, in terms of the data collected and used in
the LCA calculations, the way the LCA-based calculations have been carried
out, the presentation of environmental data in the EPD, and other additional
environmental information, as present with respect to the procedural and
methodological requirements in ISO 14025:2010 and reference standard.
I confirm that the company-specific data has been examined as regards
plausibility and consistency; the declaration owner is responsible for its
factual integrity and legal compliance.
I confirm that I have sufficient knowledge and experience of construction
products, this specific product category, the construction industry, relevant
standards, and the geographical area of the EPD to carry out this
verification.
I confirm my independence in my role as verifier; I have not been involved in
the execution of the LCA or in the development of the declaration and have no
conflicts of interest regarding this verification.
Magaly Gonzalezvazquez, as an authorized verifier acting for EPD Hub Limited
22.03.2024
References
- Lindab | For a better climate - Lindab
- Lindab - For a better climate
- Lindab - For a better climate
- Why EPD verification transparency matters
- Lindab | For a better climate - Lindab
- Lindab
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