ETP COPPER WIRE ROD
General information
EPD Owner | IBRAME INDÚSTRIA BRASILEIRA DE METAIS S/A |
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Registration number | EPD-IES-0019867:003 |
PCR | 2019:14 Construction products (EN 15804+A2) 1.3.4 |
Status | Valid |
Publication date | 2025-02-17 |
Valid until | 2030-02-16 |
EN 15804 compliant | Yes |
Geographical scope | Global, Brazil, Chile, Latin America |
Product images
Programme information
Programme | International EPD System |
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Address | EPD International AB Box 210 60 SE-100 31 Stockholm Sweden |
Website | www.environdec.com |
support@environdec.com |
Product category rules
CEN standard EN 15804 serves as the Core Product Category Rules (PCR) | |
Product Category Rules (PCR) | 2019:14 Construction products (EN 15804+A2) 1.3.4 |
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PCR review was conducted by | The Technical Committee of the International EPD System. See www.environdec.com for a list of members. Review chair: Claudia A. Peña, University of Concepción, Chile. The review panel may be contacted via the Secretariat www.environdec.com/support. |
Verification
LCA accountability | Henrique, henrique@enciclo.com.br, IBRAME INDÚSTRIA BRASILEIRA DE METAIS S/A guilherme@enciclo.com.br, guilherme@enciclo.com.br, IBRAME INDÚSTRIA BRASILEIRA DE METAIS S/A |
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Independent third-party verification of the declaration and data, according to ISO 14025:2006, via | |
Third-party verifier | Claudia A. Peña (Addere Consultores) |
Approved by | International EPD System |
Procedure for follow-up of data during EPD validity involves third party verifier | |
*EPD Process Certification involves an accredited certification body certifying and periodically auditing the EPD process and conducting external and independent verification of EPDs that are regularly published. More information can be found in the General Programme Instructions on www.envrondec.com. |
Ownership and limitation on use of EPD
Limitations
EPDs within the same product category but registered in different EPD programmes may not be comparable. For two EPDs to be comparable, they shall be based on the same PCR (including the same version number up to the first two digits) or be based on fully-aligned PCRs or versions of PCRs; cover products with identical functions, technical performances and use (e.g. identical declared/functional units); have equivalent system boundaries and descriptions of data; apply equivalent data quality requirements, methods of data collection, and allocation methods; apply identical cut-off rules and impact assessment methods (including the same version of characterisation factors); have equivalent content declarations; and be valid at the time of comparison.
Ownership
The EPD Owner has the sole ownership, liability, and responsibility for the EPD.
Information about EPD Owner
EPD Owner | IBRAME INDÚSTRIA BRASILEIRA DE METAIS S/A |
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Contact person name | CINTIA PERALI |
Contact person e-mail | epd@grupoibrame.com.br |
Organisation address | Brazil ITATIAIA 27580000 RUA TONINO BARGI, 308, BLOCOS AB, JARDIM ITAITIAIA, ITATIAIA, RIO DE JANEIRO - BRAZIL CEP 27580000 |
Description of the organisation of the EPD Owner
Ibrame Indústria Brasileira de Metais S.A. is a prominent Brazilian company specializing in the production and commercialization of non-ferrous metals, particularly copper and aluminum. Established over 65 years ago, Ibrame has become a leading player in the metal industry within Brazil. Ibrame offers a diverse range of products made from copper and aluminum. These products cater to various sectors, including construction, engineering, and manufacturing. The company emphasizes quality and innovation in its manufacturing processes to meet the demands of its clients.
Organisation logo
Product information
Product name | ETP Copper Wire Rod |
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Product identification | ETP (Electrolytic Tough Pitch) copper wire rod is a high-purity copper material known for its exceptional electrical conductivity and versatility in industrial applications. Manufactured through a process of electrolytic refining, ETP copper contains a minimum of 99.9% copper with a small oxygen content, which enhances its ability to conduct electricity efficiently. This copper grade is specifically designed for use in electrical applications, where its superior conductivity, corrosion resistance, and malleability make it a preferred choice. ETP copper wire rods are widely utilized in the production of electrical cables, transformers, motors, and other electrical components, ensuring reliable performance and longevity. |
Product description | ETP copper wire rods are the backbone of many electrical systems, owing to their unparalleled electrical properties. Their high purity ensures excellent conductivity, making them ideal for producing wires and cables used in power transmission, telecommunications, and various electrical installations. These wire rods can be easily drawn into thinner wires or shaped into custom configurations to meet specific industrial requirements. The material’s durability and resistance to corrosion further enhance its appeal, particularly in environments where long-term performance is critical. From large-scale power distribution networks to intricate wiring systems in electronic devices, ETP copper wire rods provide the essential functionality needed for efficient and reliable electrical infrastructure. |
Technical purpose of product | Copper used in drawing for the manufacture of conductors, for the most diverse applications, such as energy, automotive, telecommunications, etc. It has good ductility for drawing, extrusion and lamination processes, depending on the customer's application. |
Manufacturing or service provision description | The ETP Copper Wire Rod is made from pure cathode copper sheets which are melted in a Shaft Furnace. After melting, the molten copper is transferred to a Holding Furnace, which maintains the temperature and ensures homogenization of the liquid metal. Next, the molten copper is poured into a Tundish, a vessel designed to regulate the temperature and flow of the molten metal before the casting process. The Casting Wheel then shapes the molten copper into a continuous ingot, which is subsequently cooled, finished, and cut using an Automatic Scissor (Shear). Following the casting and cutting process, the ingots are further prepared using a Knife Process, which smooths the edges and removes any irregularities before they enter the Rolling Mill. During the rolling stage, the copper is shaped and its thickness reduced. Once rolling is complete, the copper rods undergo Pickling (to remove surface impurities) and Quenching (to cool and harden the material). Following this, a Wax Application is performed to protect the rods against oxidation. Finally, in the Coiling and Packaging phase, the copper rods are inspected for quality, coiled, and packaged using materials such as plastic film and Polyethylene Terephthalate (PET) wrapping |
Material properties | Thickness: 0.008 m |
Production site | Brazil Itatiaia 27580-000 Rua Tonino Bargi, 308 Jardim Itatiaia – Itatiaia/RJ - Brasil |
UN CPC code | 41513. Wire of copper |
Geographical scope | Global, Brazil, Chile, Latin America |
Geographical scope description | Supply chain is mainly located at Peru and Chile, manufacturing occurs in Brazil while the consumer market is also predominatly located in Brazil. |
Content declaration
Hazardous and toxic substances | The product does not contain any substances from the SVHC candidate list in concentrations exceeding 0.1% of its weight. |
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Content name | Weight, kg | Post-consumer recycled material, weight-% of product | Biogenic material, weight-% of product | Biogenic material1, kg C/declared unit |
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Primary copper | 1 | 0 | 0 | 0 |
Total | 1 | 0 | 0 | 0 |
Note 1 | 1 kg biogenic carbon is equivalent to 44/12 kg of CO2 |
Material name | Weight, kg | Weight-% (versus the product) | Biogenic material1, kg C/declared unit |
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Wood pallet | 0.02 | 2 | 0.1 |
Total | 0.02 | 2 | 0.10 |
Note 1 | 1 kg biogenic carbon is equivalent to 44/12 kg of CO2 |
LCA information
EPD based on declared or functional unit | Declared unit |
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Declared unit and reference flow | ETP Copper Wire Rod Mass: 1 kg |
Conversion factor to mass | 1 |
Are infrastructure or capital goods included in any upstream, core or downstream processes? | |
Datasources used for this EPD | ecoinvent database (general) ecoinvent 3.10 database |
LCA Software | SimaPro SimaPro 9.6 |
Additional information about the underlying LCA-based information | EF Reference Package 3.1 Time representativeness of data: January 2023 – December 2023 |
Version of the EN 15804 reference package | EF Reference Package 3.1 |
Technology description including background system | The product is the ETP (Fire-Refined High Conductivity) copper wire rod. It is a high-purity copper material known for its exceptional electrical conductivity and versatility in industrial applications produced through the smelting process, using primary copper (Cathode) as raw material. The ETP copper contains a minimum of 99.9% copper with a small oxygen content, which enhances its ability to conduct electricity efficiently. Their high purity ensures excellent conductivity, making them ideal for producing wires and cables used in power transmission, telecommunications, and various electrical installations. |
Scrap (recycled material) inputs contribution level | Less than 10% of the GWP-GHG results in modules A1-A3 come from scrap inputs |
Data quality assessment and reference years
Description of data quality assessment and reference years | Time representativeness of data: January 2023 – December 2023 |
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Electricity used in the manufacturing process in A3 | ||
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Type of electricity mix | Residual electricity mix on the market | |
Energy sources | Hydro | 34% |
Wind | 0% | |
Solar | 0% | |
Biomass | 10% | |
Geothermal | 0% | |
Waste | 0% | |
Nuclear | 4% | |
Natural gas | 15% | |
Coal | 0% | |
Oil | 3% | |
Peat | 0% | |
Other | 34% | |
GWP-GHG intensity (kg CO2 eq./kWh) | 0.21 kg CO2 eq./kWh |
System boundary
Description of the system boundary | b) Cradle to gate with options, modules C1-C4, module D and with optional modules (A1-A3 + C + D and additional modules). |
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Excluded modules | Yes, there is an excluded module, or there are excluded modules |
Justification for the omission of modules | The wire rods will be distributed to manufacturers who will apply additional processes (e.g., drawing) before further distribution and utilization in the retail market. In this context, estimating module A4 and B modules have not been included. |
Declared modules
Product stage | Construction process stage | Use stage | End of life stage | Beyond product life cycle | |||||||||||||
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Raw material supply | Transport | Manufacturing | Transport to site | Construction installation | Use | Maintenance | Repair | Replacement | Refurbishment | Operational energy use | Operational water use | De-construction demolition | Transport | Waste processing | Disposal | Reuse-Recovery-Recycling-potential | |
Module | A1 | A2 | A3 | A4 | A5 | B1 | B2 | B3 | B4 | B5 | B6 | B7 | C1 | C2 | C3 | C4 | D |
Modules declared | X | X | X | ND | X | ND | ND | ND | ND | ND | ND | ND | X | X | X | X | X |
Geography | Latin America | Global | Brazil | N/A | Brazil | N/A | N/A | N/A | N/A | N/A | N/A | N/A | Brazil | Brazil | Brazil | Brazil | Brazil |
Share of specific data | 65% | - | - | - | - | - | - | - | - | - | - | - | - | - | - | ||
Variation - products | 0% | - | - | - | - | - | - | - | - | - | - | - | - | - | - | ||
Variation - sites | 0% | - | - | - | - | - | - | - | - | - | - | - | - | - | - |
Description of the process flow diagram(s)
Cradle to gate with options, modules C1–C4, module D and with optional modules (A1–A3 + C + D and additional modules). The additional module considered is A5. The wire rods will be distributed to manufacturers who will apply additional processes (e.g., drawing) before further distribution and utilization in the retail market. In this context, estimating the transportation distance between the production facility and the end user (installation site) is unfeasible. Therefore, module A4 has not been included. Similarly, it is also unfeasible to identify or characterize any specific application for which the product will be used. Consequently, the B modules have not been included either.
Process flow diagram(s) related images
Default scenario
Name of the default scenario | Baseline |
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Description of the default scenario | Cradle to gate with options, modules C1–C4, module D and with optional modules (A1–A3 + C + D and additional modules). The additional module considered is A5. |
Module A5: Installation in the building
Explanatory name of the default scenario in module A5 | Baseline |
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Brief description of the default scenario in module A5 | Packaging waste transportation and treatment due to biogenic carbon content |
Description of the default scenario in module A5 | This module is included in the assessment due to the presence of biogenic carbon in the packaging materials Tused for the wire rods. Therefore, the key factors considered in this module include the transportation of the packaging materials and their final disposal. Following a conservative approach, it is assumed that the packaging materials are sent to a sanitary landfill for final treatment. |
Module C: End-of-life
Explanatory name of the default scenario in module C | Baseline |
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Brief description of the default scenario in module C | EoL scenario for the product |
Description of the default scenario in module C | The waste processing includes a decosntruction process, waste transportation, cable stripping and material separation. It was assumed 45.5% of copperr recycling rate. (IEA, 2021). The portion of the materials that is not recovered for recycling during waste processing is assumed to be sent to sanitary landfills. This includes fractions of copper that cannot be economically or technically processed for recovery. The disposal rates are as follows: 54.5% of the material is sent to landfill (IEA, 2021). |
Module D: Beyond product life cycle
Explanatory name of the default scenario in module D | Baseline |
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Brief description of the default scenario in module D | Product recycling |
Description of the default scenario in module D | This module represents the environmental benefits associated with the recycling of copper processed in C3. The recycled fractions of these materials are assumed to offset the production of an equivalent quantity of virgin material. The avoided impacts are calculated considering a global recycling rate (R2) of 45.5%, replacing virgin copper production (IEA, 2021). |
Environmental performance
Mandatory environmental performance indicators according to EN 15804
Impact category | Indicator | Unit | A1-A3 | A4 | A5 | B1 | B2 | B3 | B4 | B5 | B6 | B7 | C1 | C2 | C3 | C4 | D |
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Climate change - total | GWP-total | kg CO2 eq. | 7.57E+0 | ND | 4.04E-3 | ND | ND | ND | ND | ND | ND | ND | 2.15E-3 | 1.75E-2 | 6.64E-2 | 1.22E-2 | -9.72E+0 |
Climate change - fossil | GWP-fossil | kg CO2 eq. | 7.54E+0 | ND | 2.87E-4 | ND | ND | ND | ND | ND | ND | ND | 2.15E-3 | 1.63E-2 | 5.87E-2 | 1.21E-2 | -9.71E+0 |
Climate change - biogenic | GWP-biogenic | kg CO2 eq. | 2.43E-2 | ND | 3.75E-3 | ND | ND | ND | ND | ND | ND | ND | 7.68E-7 | 3.22E-4 | 5.10E-3 | 8.86E-5 | -5.90E-4 |
Climate change - land use and land-use change | GWP-luluc | kg CO2 eq. | 1.34E-2 | ND | 6.72E-6 | ND | ND | ND | ND | ND | ND | ND | 3.97E-7 | 8.53E-4 | 2.56E-3 | 1.48E-5 | -1.29E-2 |
Ozone depletion | ODP | kg CFC-11 eq. | 8.04E-8 | ND | 7.09E-12 | ND | ND | ND | ND | ND | ND | ND | 9.51E-11 | 7.34E-10 | 2.21E-9 | 2.26E-10 | -3.95E-8 |
Acidification | AP | mol H+ eq. | 8.16E-1 | ND | 2.27E-6 | ND | ND | ND | ND | ND | ND | ND | 2.05E-5 | 6.47E-5 | 2.89E-4 | 7.03E-5 | -6.28E-2 |
Eutrophication aquatic freshwater | EP-freshwater | kg P eq. | 2.24E-3 | ND | 5.60E-9 | ND | ND | ND | ND | ND | ND | ND | 1.14E-9 | 6.68E-8 | 6.13E-7 | 1.78E-7 | -2.92E-4 |
Eutrophication aquatic marine | EP-marine | kg N eq. | 2.99E-2 | ND | 1.37E-6 | ND | ND | ND | ND | ND | ND | ND | 9.93E-6 | 3.50E-5 | 1.13E-4 | 3.15E-5 | -9.80E-3 |
Eutrophication terrestrial | EP-terrestrial | mol N eq. | 4.32E-1 | ND | 1.18E-5 | ND | ND | ND | ND | ND | ND | ND | 1.09E-4 | 3.04E-4 | 1.09E-3 | 2.77E-4 | -1.08E-1 |
Photochemical ozone formation | POCP | kg NMVOC eq. | 1.33E-1 | ND | 5.36E-6 | ND | ND | ND | ND | ND | ND | ND | 3.14E-5 | 9.34E-5 | 3.50E-4 | 8.47E-5 | -3.29E-2 |
Depletion of abiotic resources - minerals and metals | ADP-minerals&metals1 | kg Sb eq. | 1.16E-2 | ND | 2.22E-11 | ND | ND | ND | ND | ND | ND | ND | 1.15E-10 | 2.32E-9 | 6.87E-9 | 3.10E-9 | 3.75E-5 |
Depletion of abiotic resources - fossil fuels | ADP-fossil1 | MJ, net calorific value | 9.07E+1 | ND | 2.79E-3 | ND | ND | ND | ND | ND | ND | ND | 2.88E-2 | 2.15E-1 | 8.95E-1 | 2.09E-1 | -8.85E+1 |
Water use | WDP1 | m3 world eq. deprived | 1.02E+1 | ND | 1.61E-5 | ND | ND | ND | ND | ND | ND | ND | 1.55E-4 | 1.74E-3 | 5.57E-2 | 0.00E+0 | -6.42E-1 |
Acronyms | GWP-fossil = Global Warming Potential fossil fuels; GWP-biogenic = Global Warming Potential biogenic; GWP-luluc = Global Warming Potential land use and land use change; ODP = Depletion potential of the stratospheric ozone layer; AP = Acidification potential, Accumulated Exceedance; EP-freshwater = Eutrophication potential, fraction of nutrients reaching freshwater end compartment; EP-marine = Eutrophication potential, fraction of nutrients reaching marine end compartment; EP-terrestrial = Eutrophication potential, Accumulated Exceedance; POCP = Formation potential of tropospheric ozone; ADP-minerals&metals = Abiotic depletion potential for non-fossil resources; ADP-fossil = Abiotic depletion for fossil resources potential; WDP = Water (user) deprivation potential, deprivation-weighted water consumption | ||||||||||||||||
General disclaimer | The results of the end-of-life stage (modules C1-C4) should be considered when using the results of the product stage (modules A1-A3/A1-A5 for services). | ||||||||||||||||
Disclaimer 1 | The results of this environmental impact indicator shall be used with care as the uncertainties of these results are high or as there is limited experience with the indicator |
Additional mandatory environmental performance indicators
Impact category | Indicator | Unit | A1-A3 | A4 | A5 | B1 | B2 | B3 | B4 | B5 | B6 | B7 | C1 | C2 | C3 | C4 | D |
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Climate change - GWP-GHG | GWP-GHG1 | kg CO2 eq. | 7.56E+0 | ND | 2.62E-3 | ND | ND | ND | ND | ND | ND | ND | 2.15E-3 | 1.72E-2 | 6.29E-2 | 1.22E-2 | -9.70E+0 |
Acronyms | GWP-GHG = Global warming potential greenhouse gas. | ||||||||||||||||
General disclaimer | The results of the end-of-life stage (modules C1-C4) should be considered when using the results of the product stage (modules A1-A3/A1-A5 for services). | ||||||||||||||||
Disclaimer 1 | The GWP-GHG indicator is termed GWP-IOBC/GHG in the ILCD+EPD+ data format. The indicator accounts for all greenhouse gases except biogenic carbon dioxide uptake and emissions and biogenic carbon stored in the product. As such, the indicator is identical to GWP-total except that the CF for biogenic CO2 is set to zero. |
Additional voluntary environmental performance indicators according to EN 15804
Impact category | Indicator | Unit | A1-A3 | A4 | A5 | B1 | B2 | B3 | B4 | B5 | B6 | B7 | C1 | C2 | C3 | C4 | D |
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Particulate matter emissions | PM | Disease incidence | 1.46E-6 | ND | 3.68E-11 | ND | ND | ND | ND | ND | ND | ND | 6.01E-10 | 1.75E-9 | 4.79E-9 | 1.26E-9 | -8.14E-7 |
Ionizing radiation - human health | IRP1 | kBq U235 eq. | 2.04E-1 | ND | 2.01E-7 | ND | ND | ND | ND | ND | ND | ND | 1.38E-6 | 1.28E-5 | 5.57E-4 | 1.65E-4 | -1.89E-2 |
Eco-toxicity - freshwater | ETP-fw2 | CTUe | 6.43E+2 | ND | 8.32E-3 | ND | ND | ND | ND | ND | ND | ND | 7.22E-4 | 8.60E-1 | 1.62E+0 | 9.60E+1 | -1.23E+1 |
Human toxicity - cancer effects | HTP-c2 | CTUh | 1.21E-7 | ND | 8.04E-13 | ND | ND | ND | ND | ND | ND | ND | 1.46E-13 | 3.92E-12 | 3.00E-11 | 1.76E-11 | -7.40E-9 |
Human toxicity - non-cancer effects | HTP-nc2 | CTUh | 1.04E-5 | ND | 2.32E-11 | ND | ND | ND | ND | ND | ND | ND | 1.71E-12 | 2.40E-10 | 7.40E-10 | 2.17E-9 | -5.29E-8 |
Land-use related impacts/soil quality | SQP2 | Dimensionless | 2.35E+2 | ND | 1.09E-2 | ND | ND | ND | ND | ND | ND | ND | 5.19E-5 | 1.74E-2 | 1.17E-1 | 3.04E-1 | -8.37E+0 |
Acronyms | PM = Potential incidence of disease due to particulate matter emissions; IRP = Potential human exposure efficiency relative to U235; ETP-fw = Potential comparative toxic unit for ecosystems; HTP-c = Potential comparative toxic unit for humans; HTP-nc = Potential comparative toxic unit for humans; SQP = Potential soil quality index. | ||||||||||||||||
General disclaimer | The results of the end-of-life stage (modules C1-C4) should be considered when using the results of the product stage (modules A1-A3/A1-A5 for services). | ||||||||||||||||
Disclaimer 1 | This impact category deals mainly with the eventual impact of low dose ionizing radiation on human health of the nuclear fuel cycle. It does not consider effects due to possible nuclear accidents, occupational exposure nor due to radioactive waste disposal in underground facilities. Potential ionizing radiation from the soil, from radon and from some construction materials is also not measured by this indicator. | ||||||||||||||||
Disclaimer 2 | The results of this environmental impact indicator shall be used with care as the uncertainties of these results are high or as there is limited experience with the indicator. |
Resource use indicators according to EN 15804
Indicator | Unit | A1-A3 | A4 | A5 | B1 | B2 | B3 | B4 | B5 | B6 | B7 | C1 | C2 | C3 | C4 | D |
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PERE | MJ, net calorific value | 2.37E+1 | ND | 2.00E-5 | ND | ND | ND | ND | ND | ND | ND | 5.22E-5 | 2.21E-3 | 2.57E-1 | 5.00E-3 | -4.45E+0 |
PERM | MJ, net calorific value | 3.30E-1 | ND | 0.00E+0 | ND | ND | ND | ND | ND | ND | ND | 0.00E+0 | 0.00E+0 | 0.00E+0 | 0.00E+0 | 0.00E+0 |
PERT | MJ, net calorific value | 2.40E+1 | ND | 2.00E-5 | ND | ND | ND | ND | ND | ND | ND | 5.22E-5 | 2.21E-3 | 2.57E-1 | 5.00E-3 | -4.45E+0 |
PENRE | MJ, net calorific value | 9.07E+1 | ND | 2.84E-3 | ND | ND | ND | ND | ND | ND | ND | 2.88E-2 | 2.21E-1 | 9.06E-1 | 2.10E-1 | -8.85E+1 |
PENRM | MJ, net calorific value | 2.41E-2 | ND | 0.00E+0 | ND | ND | ND | ND | ND | ND | ND | 0.00E+0 | 0.00E+0 | 0.00E+0 | 0.00E+0 | 0.00E+0 |
PENRT | MJ, net calorific value | 9.08E+1 | ND | 2.84E-3 | ND | ND | ND | ND | ND | ND | ND | 2.88E-2 | 2.21E-1 | 9.06E-1 | 2.10E-1 | -8.85E+1 |
SM | kg | 6.82E-2 | ND | 3.85E-9 | ND | ND | ND | ND | ND | ND | ND | 5.25E-8 | 1.85E-7 | 2.08E-6 | 1.72E-5 | 4.67E-1 |
RSF | MJ, net calorific value | 1.49E-3 | ND | 6.33E-10 | ND | ND | ND | ND | ND | ND | ND | 1.03E-8 | 2.31E-8 | 3.55E-7 | 6.81E-7 | -1.31E-4 |
NRSF | MJ, net calorific value | 0.00E+0 | ND | 0.00E+0 | ND | ND | ND | ND | ND | ND | ND | 0.00E+0 | 0.00E+0 | 0.00E+0 | 0.00E+0 | 0.00E+0 |
FW | m3 | 2.51E-1 | ND | 3.77E-7 | ND | ND | ND | ND | ND | ND | ND | 3.62E-6 | 4.08E-5 | 1.33E-3 | 0.00E+0 | -1.92E-2 |
Acronyms | 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 re-sources; SM = Use of secondary material; RSF = Use of renewable secondary fuels; NRSF = Use of non-renewable secondary fuels; FW = Use of net fresh water. | |||||||||||||||
General disclaimer | The results of the end-of-life stage (modules C1-C4) should be considered when using the results of the product stage (modules A1-A3/A1-A5 for services). |
Waste indicators according to EN 15804
Indicator | Unit | A1-A3 | A4 | A5 | B1 | B2 | B3 | B4 | B5 | B6 | B7 | C1 | C2 | C3 | C4 | D |
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HWD | kg | 3.55E+0 | ND | 2.26E-6 | ND | ND | ND | ND | ND | ND | ND | 1.88E-6 | 1.83E-4 | 1.40E-3 | 1.52E-3 | -1.99E+0 |
NHWD | kg | 2.76E+2 | ND | 2.05E-2 | ND | ND | ND | ND | ND | ND | ND | 6.20E-5 | 6.65E-4 | 4.79E-2 | 2.98E+0 | -1.23E+1 |
RWD | kg | 1.21E-4 | ND | 9.74E-11 | ND | ND | ND | ND | ND | ND | ND | 5.61E-10 | 5.07E-9 | 3.95E-7 | 1.05E-7 | -1.08E-5 |
Acronyms | HWD = Hazardous waste disposed; NHWD = Non-hazardous waste disposed; RWD = Radioactive waste disposed. | |||||||||||||||
General disclaimer | The results of the end-of-life stage (modules C1-C4) should be considered when using the results of the product stage (modules A1-A3/A1-A5 for services). |
Output flow indicators according to EN 15804
Indicator | Unit | A1-A3 | A4 | A5 | B1 | B2 | B3 | B4 | B5 | B6 | B7 | C1 | C2 | C3 | C4 | D |
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CRU | kg | 0.00E+0 | ND | 0.00E+0 | ND | ND | ND | ND | ND | ND | ND | 0.00E+0 | 0.00E+0 | 0.00E+0 | 0.00E+0 | 0.00E+0 |
MFR | kg | 5.17E-4 | ND | 1.04E-10 | ND | ND | ND | ND | ND | ND | ND | 7.26E-10 | 0.00E+0 | 2.09E-7 | 1.54E-6 | 6.76E-4 |
MER | kg | 8.40E-5 | ND | 1.12E-11 | ND | ND | ND | ND | ND | ND | ND | 3.41E-11 | 0.00E+0 | 1.40E-8 | 1.09E-8 | -1.22E-6 |
EEE | MJ, net calorific value | 1.53E-2 | ND | 3.28E-8 | ND | ND | ND | ND | ND | ND | ND | 1.73E-7 | 0.00E+0 | 5.66E-5 | 1.18E-3 | 0.00E+0 |
EET | MJ, net calorific value | 4.06E-2 | ND | 2.70E-8 | ND | ND | ND | ND | ND | ND | ND | 2.14E-7 | 0.00E+0 | 2.17E-5 | 8.06E-5 | 0.00E+0 |
Acronyms | CRU = Components for re-use; MFR = Materials for recycling; MER = Materials for energy recovery; EEE = Exported electrical energy; EET = Exported thermal energy. | |||||||||||||||
General disclaimer | The results of the end-of-life stage (modules C1-C4) should be considered when using the results of the product stage (modules A1-A3/A1-A5 for services). |
Additional environmental information
N/A
Additional social and economic information
N/A
Conversion factors
N/A
Dangerous substances to indoor air, soil, and water during the use stage
N/A
References
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International EPD System (2024) Construction products –PCR 2019:14 version 1.3.4
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International EPD System (2021) General Programme Instructions for the International EPD® System. Version 4.0
MORAIS, L. A.; NASCIMENTO, V. F.; GUASSELLI, L. A.; OMETTO, J. P. H. B. Distance estimations for municipal solid waste disposal in São Paulo State. Brazilian Journal of Cartography, v. 71, n. 4, p. 960–982, Oct./Dec. 2019. DOI: 10.14393/rbcv71n4-48611.
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Version history
Original version of the EPD, 2025-02-17