DantoPlug Super from Dantonit - Odense
General information
EPD Owner | NCC Industry AB |
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Registration number | EPD-IES-0004498:001 |
PCR | 2019:14 Construction products (EN 15804+A2) 1.3.4 |
Status | Valid |
Publication date | 2025-06-17 |
Valid until | 2030-06-16 |
EN 15804 compliant | Yes |
Geographical scope | Denmark |
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 | sofia.dahling@ncc.se, sofia.dahling@ncc.se, NCC Industry AB markus.johansson2@ncc.se, markus.johansson2@ncc.se, NCC Industry AB |
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Independent third-party verification of the declaration and data, according to ISO 14025:2006, via | |
EPD process certificate issued by | Bureau Veritas Certification Sverige AB |
Accredited by | SWEDAC |
Accredited certification body address | Sweden |
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 | NCC Industry AB |
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Contact person name | Patrik Österberg |
Contact person e-mail | patrik.osterberg@ncc.se |
Organisation address | Sweden Solna 17080 Herrjärva torg 4 |
Description of the organisation of the EPD Owner
NCC is one of the leading construction and property development companies in the Nordic region, with sales of 62 billion SEK and approximately 11 800 employees in 2024. With the Nordic region as its home market, NCC is active throughout the value chain – developing commercial properties and constructing housing, offices, industrial facilities and public buildings, roads, civil engineering structures and other types of infrastructure. NCC also offers input materials used in construction and accounts for paving and road services. NCC works to reduce both our own and our customers’ environmental impact and continues to further refine our offerings with additional products and solutions in line with this. NCC’s sustainability work is based on a holistic approach with all three dimensions of sustainability – social, environmental and economical. NCC´s sustainability framework is divided into eight impact areas: Data and expertise, Natural resources and biodiversity, Materials and circularity, Climate and energy, Health and safety, People and team, Ethics and compliance and Economic performance. NCC reports on its sustainability progress each year and the report has been included in NCC’s Annual Report since 2010. NCC applies Global Reporting Initiative (GRI) Standards, the voluntary guidelines of the GRI for the reporting of sustainability information. In addition to GRI, NCC also reports the Group’s emission of greenhouse gases to the CDP each year. NCC is a member in BSCI (Business Social Compliance Initiative), which is the broadest business-driven platform for the improvement of social compliance in the global supply chain and has been a member of the UN Global Compact since 2010. The UN Global Compact is a strategic policy initiative for businesses that are committed to aligning their operations and strategies with 10 defined and universally accepted principles in the areas of human rights, labour, environment and anti-corruption. Also visit: https://www.ncc.com/sustainability
Organisation logo
Product information
Product name | DantoPlug Super |
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Product identification | DantoPlug Super is an aggregate classified according to UN CPC 15 400. |
Product description | DantoPlug Super is manufactured at the site Dantonit - Odense operated by NCC Industry A/S in Odense, Denmark. DantoPlug is a series of bentonite pellets designed to plug and seal off boreholes. |
Product information from external sources | Read more about the product and its content in the following link: https://dantonit.group/data-sheets-reports/ As the product content is company confidential, the weights of the product contents do not reflect the actual weights. |
Technical purpose of product | DantoPlug is a series of bentonite pellets designed to plug and seal off boreholes. These pellets can completely and permanently seal a borehole and ensure that different groundwater layers are kept separated from each other. |
Manufacturing or service provision description | The raw materials extraction process at the extraction site in Tåsinge involves the extraction of bentonite clay, DantoCrude H, using heavy machinery. Once extracted, the bentonite is transported to the Dantonit factory. At the factory, the bentonite is processed into various products through a series of stages, each involving specific machinery and techniques to shape, dry, and finish the bentonite products. Unlike sand and gravel, bentonite does not produce a notable amount of dust during these processes. As such, there is almost no waste. |
Material properties | Conversion factor to mass: 0.001 LCA results per 1 kg |
Production site | Dantonit - Odense Denmark Odense S 5260 Energivej 30 |
UN CPC code | 15400. Clays |
Geographical scope | Denmark |
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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Bentonite (<99%) | 990 | 0 | 0 | 0 |
Quartz (SiO2) Respirable (<1%) | 5 | 0 | 0 | |
Cristobalite (SiO2) Respirable (<1%) | 5 | 0 | 0 | 0 |
Total | 1000 | 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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Plastics (PE, PP), wood pallet, cardboard | 19.9 | 1.99 | 16.2 |
Total | 19.90 | 1.99 | 16.20 |
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 | Aggregates Mass: 1000 kg |
Conversion factor to mass | 1 |
Are infrastructure or capital goods included in any upstream, core or downstream processes? | |
Datasources used for this EPD | GaBi database (general) GaBi Database Edition 2022, CUP 2022.01 |
LCA Software | LCA for Experts (formerly GaBi Software) N/A |
Additional information about the underlying LCA-based information | Allocation The electricity consumption is known for the production process as a whole. Allocation of electricity is made based on knowledge from the operational expert about the relative energy consumption of the machines using electricity. The fuel consumption is known for the site as a total. Allocation of the fuel consumption is made based on knowledge about which process steps each product goes through and the relative fuel consumption of each production step, based on knowledge from the operational expert. Assumptions and approximations Various oils and lubricants used in the production process, are approximated with a dataset for lubricants since no dataset or EPD were found for hydraulic oil or grease and the impact is judged to be similar. Transport distances have been approximated together with operational experts at the site, based on location of raw material supply. For the extraction of bentonite, a mobile team is carrying out the operations. Therefore, the use of lubricants, coolants and washer fluid is not specifically documented for the extraction site, but in this LCA allocated by an estimation based on the fuel use for the extraction site in relation to the total fuel use of the mobile team. For the extraction of bentonite, the generated waste is assumed by an operational expert as no documentation is available. The use of road salt is assumed by an operational expert as no documentation is available. All packaging material is combined as an average per tonne. It is difficult to know precisely what happens to the waste after being collected. It is assumed that wood, metals, plastics, paper/cardboard and oil containing waste is recycled, while other general waste is incinerated. The data provided by the manufacturer of graphite is assumed as representative for the LCA modelling and calculations. The EPD used for cement is assumed as representative for the LCA modelling and calculations, even if it follows rules of ECO Platform instead of EPD International. The EPD used for magnetite, which follows the pre-vious EN 15804:A1 and not the latest EN 15804:A1+A2, is assumed as representative for the LCA modelling and calculations. The purchased sand is assumed to be similar to the one extracted at another gravel pit, with a published EPD for the extracted gravel. The operational expert estimates that 95% of the wood pallets used for packaging the Dantonit products are new pallets, and that the remaining 5% refers to reused pallets. It is assumed that cardboard lid and paper bags are packaging with similar characteristics when performing LCA modelling and calculations. When calculating the biogenic carbon for the packaging material, which is wood based, average values are used. Cut-offs The following cut-offs have been made: –The amount of oil-contaminated soil due to spillage from machines/vehicles is very difficult to estimate. Based on internal expert knowledge, this amount is deemed negligible and very rarely occurring. –The packaging for the input materials used in the production process are negligible. –Labels for packaging, coolant and washer fluid has been neglected in the calculation since they are used in a very small amount. |
Version of the EN 15804 reference package | EF Reference Package 3.1 |
Technology description including background system | DantoPlug is a series of bentonite pellets designed to plug and seal off boreholes. The pellets are made exclusively from high qualitative Danish bentonite, excavated at the extraction site Tåsinge, in Denmark. The product is further produced using extrusion, milling/sieving, mixing with additives and finally pelletised. |
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 | Data that represent the current production process at the site are used. All input data used in the LCA model (e.g. raw materials and production data) that NCC Industry has influence over are site specific data for the production year 2022. |
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Electricity used in the manufacturing process in A3 | ||
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Type of electricity mix | Specific electricity mix as generated, or purchased from an electricity supplier, demonstrated by a contractual instrument | |
Energy sources | Hydro | 0% |
Wind | 100% | |
Solar | 0% | |
Biomass | 0% | |
Geothermal | 0% | |
Waste | 0% | |
Nuclear | 0% | |
Natural gas | 0% | |
Coal | 0% | |
Oil | 0% | |
Peat | 0% | |
Other | 0% | |
GWP-GHG intensity (kg CO2 eq./kWh) | 0.01 kg CO2 eq./kWh |
System boundary
Description of the system boundary | a) Cradle to gate with modules C1-C4 and module D (A1-A3 + C + D). |
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Excluded modules | No, there is no excluded module, or there are no excluded modules |
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 | ND | ND | ND | ND | ND | ND | ND | ND | X | X | X | X | X |
Geography | Denmark | Denmark | Denmark | N/A | N/A | N/A | N/A | N/A | N/A | N/A | N/A | N/A | Denmark | Denmark | Denmark | Denmark | Denmark |
Share of specific data | 64% | - | - | - | - | - | - | - | - | - | - | - | - | - | - | ||
Variation - products | 0% | - | - | - | - | - | - | - | - | - | - | - | - | - | - | ||
Variation - sites | 0% | - | - | - | - | - | - | - | - | - | - | - | - | - | - |
Process flow diagram(s) related images
Default scenario
Name of the default scenario | Relocation of aggregates |
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Description of the default scenario | A minor part of the aggregates are relocated, for example at the road where it is located. The material could for instance be used to fill an embankment in the proximity. This is expected to occur within a 100-year time horizon. |
Module C: End-of-life
Explanatory name of the default scenario in module C | Relocating aggregates |
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Brief description of the default scenario in module C | A minor part of the aggregates are relocated within a 100-year time horizon |
Description of the default scenario in module C | A minor part of the aggregates are relocated, for example at the road where it is located. The material could for instance be used to fill an embankment in the proximity. This is expected to occur within a 100-year time horizon. |
Module C information | Value | Unit |
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Collection process, collected separately | 1000 | kg |
Recovery system, for re-use | 1000 | kg |
Disposal, product or material for final disposal | 0 | kg |
Assumptions for scenario development, e.g. transportation | Further scenario-based information is presented in the Annex of the Background Report | N/A |
Module D: Beyond product life cycle
Explanatory name of the default scenario in module D | Replacing production |
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Brief description of the default scenario in module D | Replacing primary production of virgin aggregates |
Description of the default scenario in module D | The net load relates to the transport of the excavated material. This is assumed to be 3 km transported by a small truck (approximately 9 tonnes payload capacity). The benefit gained is equal to the virgin aggregates that are substituted. This is assumed to replace the product group with the lowest environmental impact produced at the site (module A1-A3) (conservative assumption). |
Additional scenario 1
Name of the additional scenario | Aggregates remain in construction |
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Description of the additional scenario | The majority of the aggregates (excluding the asphalt and concrete applications) stay in the construction for a long time period (more than 100 years). Thus, it is assumed that the aggregates do not reach the end-of-life stage. |
Module C: End-of-life
Description of the additional scenario in module C | The majority of the aggregates (excluding the asphalt and concrete applications) stay in the construction for a long time period (more than 100 years). Thus, it is assumed that the aggregates do not reach the end-of-life stage. |
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Module C information | Value | Unit |
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Collection process, collected separately | N/A | N/A |
Recovery system, for re-use | N/A | N/A |
Disposal, product or material for final disposal | N/A | N/A |
Assumptions for scenario development, e.g. transportation | Further scenario-based information is presented in the Annex of the Background Report | N/A |
Module D: Beyond product life cycle
Description of the additional scenario in module D | Not relevant. |
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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. | 1.41E+2 | ND | ND | ND | ND | ND | ND | ND | ND | ND | 9.38E-1 | 0.00E+0 | 0.00E+0 | 0.00E+0 | -1.43E+0 |
Climate change - fossil | GWP-fossil | kg CO2 eq. | 1.41E+2 | ND | ND | ND | ND | ND | ND | ND | ND | ND | 9.30E-1 | 0.00E+0 | 0.00E+0 | 0.00E+0 | -1.43E+0 |
Climate change - biogenic | GWP-biogenic | kg CO2 eq. | 0.00E+0 | ND | ND | ND | ND | ND | ND | ND | ND | ND | 0.00E+0 | 0.00E+0 | 0.00E+0 | 0.00E+0 | 0.00E+0 |
Climate change - land use and land-use change | GWP-luluc | kg CO2 eq. | 7.79E-2 | ND | ND | ND | ND | ND | ND | ND | ND | ND | 8.25E-3 | 0.00E+0 | 0.00E+0 | 0.00E+0 | 3.51E-3 |
Ozone depletion | ODP | kg CFC-11 eq. | 6.03E-11 | ND | ND | ND | ND | ND | ND | ND | ND | ND | 7.79E-14 | 0.00E+0 | 0.00E+0 | 0.00E+0 | 1.94E-14 |
Acidification | AP | mol H+ eq. | 2.40E-1 | ND | ND | ND | ND | ND | ND | ND | ND | ND | 2.23E-3 | 0.00E+0 | 0.00E+0 | 0.00E+0 | -3.91E-3 |
Eutrophication aquatic freshwater | EP-freshwater | kg P eq. | 1.96E-4 | ND | ND | ND | ND | ND | ND | ND | ND | ND | 3.25E-6 | 0.00E+0 | 0.00E+0 | 0.00E+0 | 1.02E-6 |
Eutrophication aquatic marine | EP-marine | kg N eq. | 6.87E-2 | ND | ND | ND | ND | ND | ND | ND | ND | ND | 9.89E-4 | 0.00E+0 | 0.00E+0 | 0.00E+0 | -1.77E-3 |
Eutrophication terrestrial | EP-terrestrial | mol N eq. | 8.39E-1 | ND | ND | ND | ND | ND | ND | ND | ND | ND | 1.11E-2 | 0.00E+0 | 0.00E+0 | 0.00E+0 | -1.93E-2 |
Photochemical ozone formation | POCP | kg NMVOC eq. | 1.98E-1 | ND | ND | ND | ND | ND | ND | ND | ND | ND | 3.18E-3 | 0.00E+0 | 0.00E+0 | 0.00E+0 | -5.82E-3 |
Depletion of abiotic resources - minerals and metals | ADP-minerals&metals1 | kg Sb eq. | 2.73E-5 | ND | ND | ND | ND | ND | ND | ND | ND | ND | 5.78E-8 | 0.00E+0 | 0.00E+0 | 0.00E+0 | 2.57E-8 |
Depletion of abiotic resources - fossil fuels | ADP-fossil1 | MJ, net calorific value | 2.44E+3 | ND | ND | ND | ND | ND | ND | ND | ND | ND | 1.21E+1 | 0.00E+0 | 0.00E+0 | 0.00E+0 | -1.94E+1 |
Water use | WDP1 | m3 world eq. deprived | 2.30E+1 | ND | ND | ND | ND | ND | ND | ND | ND | ND | 1.03E-2 | 0.00E+0 | 0.00E+0 | 0.00E+0 | -7.11E-3 |
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. | 1.41E+2 | ND | ND | ND | ND | ND | ND | ND | ND | ND | 9.45E-1 | 0.00E+0 | 0.00E+0 | 0.00E+0 | -1.43E+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 | 1.22E-3 | ND | ND | ND | ND | ND | ND | ND | ND | ND | 1.47E-4 | 0.00E+0 | 0.00E+0 | 0.00E+0 | -3.62E-4 |
Ionizing radiation - human health | IRP1 | kBq U235 eq. | 1.55E+0 | ND | ND | ND | ND | ND | ND | ND | ND | ND | 2.26E-3 | 0.00E+0 | 0.00E+0 | 0.00E+0 | -5.39E-3 |
Eco-toxicity - freshwater | ETP-fw2 | CTUe | 1.35E+3 | ND | ND | ND | ND | ND | ND | ND | ND | ND | 8.53E+0 | 0.00E+0 | 0.00E+0 | 0.00E+0 | -1.49E+1 |
Human toxicity - cancer effects | HTP-c2 | CTUh | 3.32E-8 | ND | ND | ND | ND | ND | ND | ND | ND | ND | 8.66E-10 | 0.00E+0 | 0.00E+0 | 0.00E+0 | -1.60E-9 |
Human toxicity - non-cancer effects | HTP-nc2 | CTUh | 2.12E-6 | ND | ND | ND | ND | ND | ND | ND | ND | ND | 2.51E-7 | 0.00E+0 | 0.00E+0 | 0.00E+0 | -4.72E-7 |
Land-use related impacts/soil quality | SQP2 | Dimensionless | 5.09E+3 | ND | ND | ND | ND | ND | ND | ND | ND | ND | 5.05E+0 | 0.00E+0 | 0.00E+0 | 0.00E+0 | 2.08E+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 | 6.74E+2 | ND | ND | ND | ND | ND | ND | ND | ND | ND | 8.57E-1 | 0.00E+0 | 0.00E+0 | 0.00E+0 | -3.95E-1 |
PERM | MJ, net calorific value | 0.00E+0 | ND | ND | 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 | 6.74E+2 | ND | ND | ND | ND | ND | ND | ND | ND | ND | 8.57E-1 | 0.00E+0 | 0.00E+0 | 0.00E+0 | -3.95E-1 |
PENRE | MJ, net calorific value | 2.44E+3 | ND | ND | ND | ND | ND | ND | ND | ND | ND | 1.21E+1 | 0.00E+0 | 0.00E+0 | 0.00E+0 | -1.95E+1 |
PENRM | MJ, net calorific value | 0.00E+0 | ND | ND | 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 | 2.44E+3 | ND | ND | ND | ND | ND | ND | ND | ND | ND | 1.21E+1 | 0.00E+0 | 0.00E+0 | 0.00E+0 | -1.95E+1 |
SM | kg | 0.00E+0 | ND | ND | ND | ND | ND | ND | ND | ND | ND | 0.00E+0 | 0.00E+0 | 0.00E+0 | 0.00E+0 | 0.00E+0 |
RSF | MJ, net calorific value | 0.00E+0 | ND | ND | ND | ND | ND | ND | ND | ND | ND | 0.00E+0 | 0.00E+0 | 0.00E+0 | 0.00E+0 | 0.00E+0 |
NRSF | MJ, net calorific value | 0.00E+0 | ND | ND | ND | ND | ND | ND | ND | ND | ND | 0.00E+0 | 0.00E+0 | 0.00E+0 | 0.00E+0 | 0.00E+0 |
FW | m3 | 6.02E-1 | ND | ND | ND | ND | ND | ND | ND | ND | ND | 9.44E-4 | 0.00E+0 | 0.00E+0 | 0.00E+0 | 3.38E-5 |
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 | 8.34E-3 | ND | ND | ND | ND | ND | ND | ND | ND | ND | 4.49E-11 | 0.00E+0 | 0.00E+0 | 0.00E+0 | -6.03E-9 |
NHWD | kg | 3.09E+0 | ND | ND | ND | ND | ND | ND | ND | ND | ND | 1.75E-3 | 0.00E+0 | 0.00E+0 | 0.00E+0 | -2.85E-2 |
RWD | kg | 1.09E-2 | ND | ND | ND | ND | ND | ND | ND | ND | ND | 1.57E-5 | 0.00E+0 | 0.00E+0 | 0.00E+0 | -3.66E-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 |
---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|
CRU | kg | 0.00E+0 | ND | ND | ND | ND | ND | ND | ND | ND | ND | 1.00E+3 | 0.00E+0 | 0.00E+0 | 0.00E+0 | 0.00E+0 |
MFR | kg | 7.96E-1 | ND | ND | ND | ND | ND | ND | ND | ND | ND | 0.00E+0 | 0.00E+0 | 0.00E+0 | 0.00E+0 | 0.00E+0 |
MER | kg | 1.72E+1 | ND | ND | ND | ND | ND | ND | ND | ND | ND | 0.00E+0 | 0.00E+0 | 0.00E+0 | 0.00E+0 | -2.64E-2 |
EEE | MJ, net calorific value | 0.00E+0 | ND | ND | ND | ND | ND | ND | ND | ND | ND | 0.00E+0 | 0.00E+0 | 0.00E+0 | 0.00E+0 | 0.00E+0 |
EET | MJ, net calorific value | 0.00E+0 | ND | ND | ND | ND | ND | ND | ND | ND | ND | 0.00E+0 | 0.00E+0 | 0.00E+0 | 0.00E+0 | 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). |
Dangerous substances to indoor air, soil, and water during the use stage
The product does not contain any substances of very high concern (SVHC) according to REACH.
References
Annex to General Background Report, Aggregates, Site specific information for aggregates from the site Dantonit – Odense, 2022. Version 2025-06-17.
EN 15804:2012+A2:2019/AC:2021: Sustainability of construction works - Environmental Product Declarations - Core rules for the product category of construction products.
EPD International (2021) General Programme Instructions for the International EPD® System, version 4.0, dated 2021-03-29. www.environdec.com
EPD process – general description (2024) NCC Industry, Division Stone Materials
Environmental Product Declaration (S-P-02060) for product MagnaDense 8s & MagnaDense 20s from LKAB Minerals AB.
Environmental Product Declaration (declaration number: IBU-CEI-HOL-2203120-DE2022000132-1SUG001-DE) for product Cement Holcim Sulfo 5 R, from Holcim (Deutschland) GmbH.
Environmental Product Declaration (S-P-05226) for aggregates from Sellebjerg gravel pit – Stenstrup, from NCC Industry AB.
General background report, Environmental Product Declarations for Aggregates. Version 2024-04-05.
Geological Survey of Sweden (2017) Grus, sand och krossberg. 2018:2.
MinBaS II (2011). Undersökning av eventuella effekter på vegetation av damning från täktverksamhet – Slutrapport. MinBaS II område nr 3, Delområde nr 3.1a, Delprojekt nr 3.1a-4. Rapport nr 3.1a-4.
Product Category Rules PCR 2019:14 Construction products, version 1.3.3 of 2024-03-01
Regulation (EU) no. 305/2011 – Construction Products Regulation (CPR), https://eur-lex.europa.eu/ LexUriServ/LexUriServ.do?uri=OJ:L:2011:088:0005:0043:EN:PDF
SS-EN ISO 14025:2010 Environmental labels and declarations - Type III environmental declarations - Principles and procedures (ISO 14025:2006)
SS-EN ISO 14040:2006 Environmental management – Life cycle assessment – Principles and framework (ISO 14040:2006). Including Amd 1:2020.
SS-EN ISO 14044:2006 Environmental management - Life cycle assessment - Requirements and guidelines. Including Amd 1:2018 and Amd 2:2020.
The International EPD® System, EPD International AB, Stockholm, Sweden, http://www.environdec.com/
United Nations Statistics Division (2015). Central Product Classification, version 2.1. https://unstats.un.org/unsd/ classifications/unsdclassifications/cpcv21.pdf.
UEPG (European Aggregates Association) (2018). Annual Review 2017-2018, A Sustainable Industry for a Sustainable Europe. http://www.uepg.eu/uploads/ Modules/Publications/uepg-annual-review-2017-2018.pdf.
Safety data sheets and certificates. https://dantonit.group/safety-data-sheets/.