EPD-IES-0019963:001

Raw moraine from Halmstad quarry - Biskopstorp

The product consist of moraine and can for example be used in civil engineering work and road construction

General information

EPD Owner	NCC Industry AB
Registration number	EPD-IES-0019963:001
PCR	2019:14 Construction products (EN 15804+A2) 1.3.4
Status	Valid
Publication date	2025-05-14
Valid until	2030-05-13
EN 15804 compliant	Yes
Geographical scope	Sweden

Product images

Programme information

Programme	International EPD System
Address	EPD International AB Box 210 60 SE-100 31 Stockholm Sweden
Website	www.environdec.com
E-mail	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
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	markus.johansson2@ncc.se, markus.johansson2@ncc.se, NCC Industry AB sofia.dahling@ncc.se, sofia.dahling@ncc.se, NCC Industry AB
Independent third-party verification of the declaration and data, according to ISO 14025:2006, via	EPD verification through an individual EPD verification EPD verification through EPD Process Certification* EPD verification through a pre-verified LCA/EPD tool
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	Yes No
*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
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	Raw moraine
Product identification	The product is an aggregate classified according to UN CPC 15 320.
Product description	The product consist of moraine and can for example be used in civil engineering work and road construction
Technical purpose of product	The product can for example be used in civil engineering work and road construction
Manufacturing or service provision description	The moraine is extracted from the quarry site using heavy machinery. This involves removing the overburden and then excavating the moraine material.
Material properties	Conversion factor to mass: 0.001 LCA results per 1 kg
Production site	Halmstad quarry - Biskopstorp Sweden Kvibille 305 78 Biskopstorp 117
UN CPC code	15320. Pebbles, gravel, broken or crushed stone, macadam; granules, chippings and powder of stone
Geographical scope	Sweden

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.

Product content
Content name	Weight, kg	Post-consumer recycled material, weight-% of product	Biogenic material, weight-% of product	Biogenic material¹, kg C/declared unit
Excavated surplus rock	1000	0	0	0
Total	1000	0	0	0
Note 1	1 kg biogenic carbon is equivalent to 44/12 kg of CO₂

Packaging materials
Material name	Weight, kg	Weight-% (versus the product)	Biogenic material¹, kg C/declared unit
N/A	1	0	0
Total	1	0	0
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
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?	Yes No
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	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. Since the only available data of explosives are aggregated figures of both emulsion slurry and dynamite, and since there only exist one data set of explosives in Sphera, the same data set are used for these two types of explosives. Fuse heads for igniting explosives and fuse cables are estimated based on values from another site, since there are no current data available. Data regarding the consumption of lubricant, grease and glycol is based on aggregated data for Biskopstorp and two nearby quarries. Biskopstorp is assumed, based on the knowledge of operational experts, to account for a majority of the total consumption among the three quarries. In this way, the consumption of lubricant, grease and glycol in Biskopstorp is calculated. However, regarding the consumption of lubricant, grease, and as well washer fluid, for drilling rigs in Biskopstorp, the data is based on standard values of volumes consumed per drilling meter. The total number of drill meters is obtained using blast journals from the data collection period. The amount of water used in various processes is estimated based on values from another site, since there are no current data available. The consumption of AdBlue for yellow machines is based on data from invoices. For other machines and external machines used, where invoices are not available, an assumption is made with the help of a machine operator. Data on waste are based on invoices from waste management companies. Concerning landfill waste, the total amount, according to operational experts, is aggregated over approximately a five-year period and thus not representative of a normal year. Thus, the total amount of landfill waste is divided by 5. Furthermore, the total amount of landfill waste is also based on data from Biskopstorp and two nearby quarries. The assessment of operational experts is that Biskopstorp is responsible for a majority of the total amount of waste. The waste category “Hazardous waste”, containing oil- and fuel filters, is assumed to be incinerated. Regarding mixed waste, the total given volume is accumulated over several years and therefore not representative for 2022. Based on the knowledge of operational experts 50% of this total volume of mixed waste can be derived from the data collection period 2022. Following a conservative approach, the mixed waste is assumed to be metal waste. The wear of manganese steel from crushers is estimated based on values from another site, since there are no current data available. Allocation The consumption of explosives is allocated equally on all products originating from blasted rock, based on mass. Explosives are not allocated to products not originating from blasted rock. The electricity consumption is known based on data from the secondary crushing and third stage crushing process steps. Included in the electricity use for the third stage crusher is electricity use for office, workshop, and heated storage. However, there is no data on how large this proportion is, and in this case this proportion is therefore assumed based on the knowledge from operational experts. In this way, the electricity use per process step is calculated. The fuel consumption is known for the site as a total. Allocation of fuel consumption is therefore mainly done based on mass of each product produced at the site. A part of the total amount of diesel are however directly linked to the production of asphalt at the site, and therefore this amount of diesel is not considered. In addition to the total amount of fuel for the entire plant, however, a small part of the fuel consumption can be derived to specific process steps, for blasting and primary crushing. The allocation of this fuel is done based on data of the fuel consumption in these process steps, as well as the knowledge from operational expert about which process steps each product goes through. Cut-offs – 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. – Glycol, used for antifreeze liquid preservation on engines, is used little and rarely, so it is not included in the calculation. – Washer fluid used in machines are excluded from the calculation since it is used in a very small amount. – Fuse heads used for igniting explosives are excluded from the calculation since those are used in a very small amount. – Fuse cables used for igniting explosives are excluded from the calculation since those are used in a very small amount.
Version of the EN 15804 reference package	EF Reference Package 3.1
Technology description including background system	The product is an aggregate consisting of moraine. The product can be used for e.g. as filling material in civil engineering.
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.

Electricity data

Electricity used in the manufacturing process in A3
Type of electricity mix	Specific electricity mix as generated, or purchased from an electricity supplier, demonstrated by a contractual instrument
Energy sources	Hydro	100%
	Wind	0%
	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).
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
	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	Sweden	Sweden	Sweden	N/A	N/A	N/A	N/A	N/A	N/A	N/A	N/A	N/A	Sweden	Sweden	Sweden	Sweden	Sweden
Share of specific data	47%			-	-	-	-	-	-	-	-	-	-	-	-	-	-
Variation - products	0%			-	-	-	-	-	-	-	-	-	-	-	-	-	-
Variation - sites	0%			-	-	-	-	-	-	-	-	-	-	-	-	-	-

Process flow diagram(s) related images

Additional scenario 0

Name of the additional scenario	Aggregates remain in construction
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.

Module C information	Value	Unit
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.

Default scenario

Name of the default scenario	Relocation of aggregates
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
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
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
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).

Environmental performance

The estimated impact results are only relative statements, which do not indicate the endpoints of the impact categories, exceeding threshold values, safety margins and/or risks.

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
Climate change - total	GWP-total	kg CO₂ eq.	3.90E+0	ND	ND	ND	ND	ND	ND	ND	ND	ND	9.38E-1	0.00E+0	0.00E+0	0.00E+0	-1.92E+0
Climate change - fossil	GWP-fossil	kg CO₂ eq.	3.88E+0	ND	ND	ND	ND	ND	ND	ND	ND	ND	9.30E-1	0.00E+0	0.00E+0	0.00E+0	-1.92E+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.	1.88E-2	ND	ND	ND	ND	ND	ND	ND	ND	ND	8.25E-3	0.00E+0	0.00E+0	0.00E+0	2.59E-3
Ozone depletion	ODP	kg CFC-11 eq.	2.03E-13	ND	ND	ND	ND	ND	ND	ND	ND	ND	7.79E-14	0.00E+0	0.00E+0	0.00E+0	-5.06E-13
Acidification	AP	mol H⁺ eq.	1.22E-2	ND	ND	ND	ND	ND	ND	ND	ND	ND	2.23E-3	0.00E+0	0.00E+0	0.00E+0	-8.76E-3
Eutrophication aquatic freshwater	EP-freshwater	kg P eq.	7.85E-6	ND	ND	ND	ND	ND	ND	ND	ND	ND	3.25E-6	0.00E+0	0.00E+0	0.00E+0	3.22E-7
Eutrophication aquatic marine	EP-marine	kg N eq.	5.57E-3	ND	ND	ND	ND	ND	ND	ND	ND	ND	9.89E-4	0.00E+0	0.00E+0	0.00E+0	-3.53E-3
Eutrophication terrestrial	EP-terrestrial	mol N eq.	6.20E-2	ND	ND	ND	ND	ND	ND	ND	ND	ND	1.11E-2	0.00E+0	0.00E+0	0.00E+0	-4.33E-2
Photochemical ozone formation	POCP	kg NMVOC eq.	1.34E-2	ND	ND	ND	ND	ND	ND	ND	ND	ND	3.18E-3	0.00E+0	0.00E+0	0.00E+0	-1.02E-2
Depletion of abiotic resources - minerals and metals	ADP-minerals&metals¹	kg Sb eq.	2.06E-7	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	5.38E+1	ND	ND	ND	ND	ND	ND	ND	ND	ND	1.21E+1	0.00E+0	0.00E+0	0.00E+0	-2.68E+1
Water use	WDP¹	m³ world eq. deprived	8.59E-2	ND	ND	ND	ND	ND	ND	ND	ND	ND	1.03E-2	0.00E+0	0.00E+0	0.00E+0	-9.64E-2
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
Climate change - GWP-GHG	GWP-GHG¹	kg CO₂ eq.	3.96E+0	ND	ND	ND	ND	ND	ND	ND	ND	ND	9.45E-1	0.00E+0	0.00E+0	0.00E+0	-1.91E+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
Particulate matter emissions	PM	Disease incidence	3.74E-4	ND	ND	ND	ND	ND	ND	ND	ND	ND	1.47E-4	0.00E+0	0.00E+0	0.00E+0	-3.88E-4
Ionizing radiation - human health	IRP¹	kBq U235 eq.	1.21E-2	ND	ND	ND	ND	ND	ND	ND	ND	ND	2.26E-3	0.00E+0	0.00E+0	0.00E+0	-2.00E-2
Eco-toxicity - freshwater	ETP-fw²	CTUe	3.91E+1	ND	ND	ND	ND	ND	ND	ND	ND	ND	8.53E+0	0.00E+0	0.00E+0	0.00E+0	-1.86E+1
Human toxicity - cancer effects	HTP-c²	CTUh	2.15E-9	ND	ND	ND	ND	ND	ND	ND	ND	ND	8.66E-10	0.00E+0	0.00E+0	0.00E+0	-1.80E-9
Human toxicity - non-cancer effects	HTP-nc²	CTUh	5.13E-7	ND	ND	ND	ND	ND	ND	ND	ND	ND	2.51E-7	0.00E+0	0.00E+0	0.00E+0	-5.18E-7
Land-use related impacts/soil quality	SQP²	Dimensionless	1.16E+1	ND	ND	ND	ND	ND	ND	ND	ND	ND	5.05E+0	0.00E+0	0.00E+0	0.00E+0	1.31E+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
PERE	MJ, net calorific value	2.68E+0	ND	ND	ND	ND	ND	ND	ND	ND	ND	8.57E-1	0.00E+0	0.00E+0	0.00E+0	-8.00E-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	2.68E+0	ND	ND	ND	ND	ND	ND	ND	ND	ND	8.57E-1	0.00E+0	0.00E+0	0.00E+0	-8.00E-1
PENRE	MJ, net calorific value	5.39E+1	ND	ND	ND	ND	ND	ND	ND	ND	ND	1.21E+1	0.00E+0	0.00E+0	0.00E+0	-2.69E+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	5.39E+1	ND	ND	ND	ND	ND	ND	ND	ND	ND	1.21E+1	0.00E+0	0.00E+0	0.00E+0	-2.69E+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	1.48E-2	ND	ND	ND	ND	ND	ND	ND	ND	ND	9.44E-4	0.00E+0	0.00E+0	0.00E+0	-1.35E-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
HWD	kg	2.00E-3	ND	ND	ND	ND	ND	ND	ND	ND	ND	4.49E-11	0.00E+0	0.00E+0	0.00E+0	-2.00E-3
NHWD	kg	2.42E-2	ND	ND	ND	ND	ND	ND	ND	ND	ND	1.75E-3	0.00E+0	0.00E+0	0.00E+0	-2.11E-2
RWD	kg	8.25E-5	ND	ND	ND	ND	ND	ND	ND	ND	ND	1.57E-5	0.00E+0	0.00E+0	0.00E+0	-1.21E-4
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	5.01E-2	ND	ND	ND	ND	ND	ND	ND	ND	ND	0.00E+0	0.00E+0	0.00E+0	0.00E+0	-5.01E-2
MER	kg	1.20E-2	ND	ND	ND	ND	ND	ND	ND	ND	ND	0.00E+0	0.00E+0	0.00E+0	0.00E+0	-1.20E-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 products does not contain any substances of very high concern (SVHC) according to REACH.

References

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