Declaratie de mediu pentru gleturi si tencuieli - conform EN 15804 si ISO 14025 Saint-Gobain Rigips
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ENVIRONMENTAL PRODUCT DECLARATION
In accordance with EN 15804 and ISO 14025
Rigips plasters
Date of issue: 2019-02-27
Validity: 5 years
Valid until: 2024-01-31
Scope of the EPD®: Romania
Registration number
The International EPD® System:
S-P-01370
General information
Manufacturer: Saint-Gobain Construction Products Romania, Rigips Business Unit, Turda Plasters Plant
Programme used: International EPD System http://www.environdec.com/
EPD registration number/declaration number: S-P-01370
PCR identification: EN 15804 Sustainability of construction works – Environmental product declaration - core
rules for the product category of construction product and The International EPD® System PCR 2012:01 version
2.3 for Construction products and Construction services with reference to sub PCR-A-Mortars applied to a
surface (construction product) version 2018
Site of manufacture: Turda Plasters Plant / Saint-Gobain Construction Products Romania, Rigips Business Unit
Owner of the declaration
: Saint-Gobain Construction Products Romania Rigips Business Unit
Product / product family name and manufacturer represented: Gypsum Plasters covering 4 products
(Rimano UNI, Rimano TEN, Rimano Bianco, Rigips Super)
UN CPC code: 37410 Plaster
Declaration issued: 2019-02-27
Valid until: 2024-01-31
Demonstration of verification: an independent verification of the declaration was made, according to ISO
14025:2010. This verification was external and conducted by the following third party: Andrew NORTON,
Renuables, based on the PCR mentioned above.
EPD Prepared by: Central TEAM, Saint-Gobain Gypsum. Contact: Alina Cismas from Saint-Gobain Contruction
Products Romania Rigips Business Unit (Alina.Cismas@saint-gobain.com) and Patricia Jimenez Diaz from LCA
central team (Patricia.JimenezDiaz@saint-gobain.com)
Gypsum plasters addressed in this EPD are manufactured by Saint-Gobain Construction Products Romania,
Rigips Business Unit at Turda Plasters Plant according to Harmonized European Standard
s:
- EN 13279-1:2008 – Gypsum binders and gypsum plasters. Part.1: Definitions and requirements
- EN 13963:2005 - Jointing materials for gypsum plasterboards — Definitions, requirements and test
methods
Harmonized European standards address all of the Essential Requirements of the European Construction
Products Regulation No. 305/2011.
Declaration of Hazardous substances: (Candidate list of Substances of Very High Concern): none
Certifications held at plant:
Environmental Management System in place at site: ISO 14001:2015 certificate N°: 10114382
Energy Management System in place at site: ISO 50001/2001 – certificate N° 00009790
Quality Management System in place at site: ISO 9001:2015 - certificate N°: 10114364
Occupational Health and Safety Management System in place at site: OHSAS 18001:2007 – certificate N° 0040391
The EPD is based on 2017 production data for the Turda site producing Gypsum plasters: Rimano UNI, Rimano
TEN, Rimano Bianco and Rigips Super. This EPD cove
rs information modules A1 to C4 (cradle to gate with
options) as defined in EN 15804:2012 + A1:2013.
The declared unit is 1 kg of Rigips plaster delivered in powder.
Geographical scope of the EPD®: Romania
EPDs of construction products may not be comparable if they do not comply with EN 15804.
CEN standard EN 15804 serves as the core PCR
a
PCR:
PCR 2012:01 Construction products and Construction services, Version 2.3
PCR review was conducted
by:
The Technical Committee of the International EPD® System. Chair:
Massimo Marino.
Contact via info@environdec.com
Independent verification of the declaration, according to EN ISO 14025:2010
Internal ☐ External ☒
Third party verifier:
Andrew Norton , Renuables http://renuables.co.uk
Accredited or approved by
The International EPD System
1
Product description
Product description and use:
This Environmental Product Declaration (EPD®) covers four products, Rimano UNI, Rimano TEN, Rimano
Bianco and Rigips Super for indoor use.
RIMAN
O UNI complies with EN 13279-1:2008 standard, type B4/50/2.
RIMANO TEN complies with EN 13279-1:2008 standard, type C4/20.
RIMANO BIANCO complies with EN 13279-1:2008 standard, type B1/20/2.
RIGIPS SUPER complies with EN 13963:2005, type 3B.
®
®
Rigips and Rimano plasters are made up of hemihydrate calcium sulphate (80-97%) and additives &
aggregates (which provide the product specific characteristic of performance) as described in the below table..
Natural gypsum
Additives &
aggregates
Rimano TEN
Rimano UNI
97%
80%
Rimano
Bianco
87%
3%
20%
13%
Rigips Super
88%
12%
The packaging used is a polyethylene bag that contains 25 kg bagged Rimano UNI, 25 kg bagged Rimano TEN,
20 kg bagged Rimano Bianco, 5kg and 25 kg bagged Rigips Super.
The EPD describes the environmental impacts of 1 kg of Rigips plaster, delivered in powder for indoor wall
applications, it represents the worst case scenario among the four plaster products.
Description of the main components and/or materials f
or 1kg of reference product for the calculation of
the EPD®:
PARAMETER
VALUE (expressed per declared unit)
Quantity of plaster
Packaging for the transportation and distribution
Product used for the Installation
1 Kg
Polyethylene bag: 3.79 g/kg
Wooden pallet: 25 g/kg
Stretch hood: 0.53 g/kg
Ink: 0.00081 g/kg
Adhesive: 0.008 g/kg
Label: 0.00142 g/kg
Cardboard: 0.3 g/kg
Water: 0.8 l/kg
Energy consumption: 0.021 MJ/kg
During the life cycle of the product no hazardous substance listed in the “Candidate List of Substances of Very
High Concern (SVHC) for authorization” has been used in a percentage higher than 0,1% of the weight of the
product.
The verifier and the program operator do not make any claim nor have any responsibility of the legality of the
product.
2
LCA calculation information
EPD TYPE DECLARED
DECLARED UNIT
SYSTEM BOUNDARIES
REFERENCE SERVICE LIFE (RSL)
CUT-OFF RULES
ALLOCATIONS
GEOGRAPHICAL COVERAGE
AND TIME PERIOD
PRODUCT CPC CODE
Cradle to gate with option
s
1 kg of Rigips plaster delivered in powder
Cradle to Gate with options: stages A1 – A3, A4 – A5, B1 – B7, C1 –
C4
50 years
By default, it corresponds to Standards building design life and value is
included in Appendix III of Saint-Gobain Environmental Product
Declaration Methodological Guide for Construction Products.
Life Cycle Inventory data for a minimum of 99% of total inflows to the
upstream and core module shall be included
Production data.
Recycling, energy and waste data have been calculated on a mass
basis.
Scope includes: Romania
Data included is collected from one production site in Turda Plasters
Plant, Saint-Gobain Construction Products Romania, Rigips Business
Unit
Data collected for the year 2017.
Full life cycle study.
Background data: Ecoinvent (from 2015 to 2016) and GaBi ( from
2013 to 2016)
37410 Plaster
According to EN 15804, EPDs of construction products may not be comparable if they do not comply with this standard.
According to ISO 21930, EPDs might n
ot be comparable if they are from different programmes.
3
Life cycle stages
Flow diagram of the Life Cycle
Product stage, A1-A3
Description of the stage: the product stage of plaster products is subdivided into 3 modules A1, A2 and A3
respectively “Raw material supply”, “transport to manufacturer” and “manufacturing”.
A1, raw material supply.
This includes the extraction and processing of all raw materials and energy which occur upstream from the
manufacturing process.
A2, transport to the manufacturer.
The raw materials are transported to the manufacturing site. The modelling includes road, boat and/or train
transportations of each raw material.
A3, manufacturing.
This module includes the manufacture of products and the manufacture of packaging. The production of
packaging material is taken into account at this stage. The processing of any waste arising from this stage is
also included.
4
Manufacturing process flow diagram
Gypsum
extraction and
transport
Packa
ging
manufacture
and transport
Crushing
Calcination/
dehydration
Milling /
grinding
Packaging
Additive
addition
and mixing
Screening
Finished
product
Additives
manufacture
and transport
Manufacturing in detail:
Gypsum rock is open pit quarried by drilling and blasting, then transported to a crushing plant where it is crushed,
screened and stockpiled according to its quality. The stockpiled ore transported by trucks to manufacturing
factory is first crushed to reduce rocks size and further dehydrated in calcining kilns to produce hemihydrate
(stucco). Stucco is further ground to obtain a specific surface area and then screened to remove any particles
that are too large. In the manufacture of plasters, stucco is batch mixed with additives and aggregates to produce
finished product. The thoroughly mixed plaster is fed to a bagging operation.
Gypsum waste is reintegrated back into the manufacturing process wherever possible.
Construction process stage, A4-A5
Description of the sta
ge: the construction process is divided into 2 modules: A4, transport to the building site and
A5, installation in the building
A4, transport to the building site.
This module includes transport from the production gate to the building site. Transport is calculated on the basis
of a scenario with the parameters described in the following table.
PARAMETER
VALUE (expressed per declared unit)
Fuel type and consumption of vehicle or vehicle type
used for transport e.g. long distance truck, boat, etc.
Long distance truck, maximum load weight of 24 t and
consumption of 0.35 liters per km
Distance
380 km
Capacity utilisation (including empty returns)
42.5 %
Bulk density of transported products
Volume capacity utilisation factor
570 – 640 kg/m
1
5
3
A5, installation into the building.
The accompanying table quantifies the parameters for installing the product at the building site. All installation
materials and their waste processing are included.
PARAMETER
VALUE (expressed per
declared unit)
Ancillary materials for installation
(specified by materials)
Water use
Other resource use
Quantitative description of energy type (regional mix)
and consumption during the installation process
Wastage of materials on the building site before waste
processing, generated by the product’s installation
(specified by type)
Output materials (specified by type) as results of waste
processing at the building site e.g. of collection for
recycling, for energy recovering, disposal
(specified by route)
Direct emissions to ambient air, soil and water
None
0.8 liters/kg
None
0.021 MJ/kg
Plaster with water: 5%
Plaster: 5% to landfill
Polyethylene bag: 3.79 g/kg to landfill
Wooden pallet: 25 g/kg to recovery
Stretch hood: 0.53 g/kg to landfill
Ink: 0.00081 g/kg to landfill
Adhesive: 0.008 g/kg to landfill
Label: 0.00142 g/kg to landfill
Cardboard: 0.3 g/kg to landfill
Water emission to air (0.624 l/kg)
Use stage (excluding potential savings), B1-B7
Description of the stage:
Th
e use stage, related to the building fabric includes:
B1, use or application of the installed product;
B2, maintenance;
B3, repair;
B4, replacement;
B5, refurbishment;
B6, operational energy use
B7, operational water use
Description of scenarios and additional technical information:
The product has a reference service life of 50 years. This assumes that the product will last in situ with no
requirements for maintenance, repair, replacement or refurbishment throughout this period. Therefore, it has no
impact at this stage.
Maintenance:
PARAMETER
VALUE (expressed per declared unit)
Maintenance process
None required during product lifetime
Maintenance cycle
Ancillary materials for maintenance (e.g. cleaning agent,
specify materials)
Wastage material during maintenance (specify
materials)
None required during product lifetime
Net fresh water consumption during maintenance
None required during product lifetime
Energy input during maintenance
(e.g. vacuum cleaning), energy carrier ty
pe, (e.g.
electricity) and amount, if applicable
and relevant
None required during product lifetime
None required during product lifetime
None required during product lifetime
6
Repair:
PARAMETER
VALUE (expressed per declared unit)
Repair process
None required during product lifetime
Inspection process
None required during product lifetime
Repair cycle
None required during product lifetime
Ancillary materials
(e.g. lubricant, specify materials)
Wastage material during repair
(specify materials)
None required during product lifetime
None required during product lifetime
Net fresh water consumption during repair
None required during product lifetime
Energy input during repair (e.g. crane activity), energy
carrier type, (e.g. electricity) and amount if applicable
and relevant
None required during product lifetime
Replacement:
PARAMETER
VALUE (expressed per declared unit)
Replacement cycle
Energy input during replacement (e.g. crane activity),
energy carrier type, (e.g.
electricity) and amount if
applicable and relevant
Exchange of worn parts during the product’s life cycle
(e.g. zinc galvanized steel sheet), specify materials
None required during product lifetime
None required during product lifetime
None required during product lifetime
Refurbishment:
PARAMETER
VALUE (expressed per declared unit)
Refurbishment process
None required during product lifetime
Refurbishment cycle
None required during product lifetime
Material input for refurbishment (e.g. bricks), including
ancillary materials for the refurbishment process (e.g.
lubricant, specify materials)
Wastage material during refurbishment (specify
materials)
Energy input during refurbishment (e.g. crane activity),
energy carrier type, (e.g. electricity) and amount
Further assumptions for scenario development (e.g.
frequency and time period of use, number of occupants)
None required during product lifetime
None required during product lifetime
None required during product lifetime
None
required during product lifetime
7
Use of energy and water:
PARAMETER
VALUE (expressed per declared unit)
Ancillary materials specified by material
None required during product lifetime
Net fresh water consumption
None required during product lifetime
Type of energy carrier (e.g. electricity, natural gas,
district heating)
None required during product lifetime
Power output of equipment
None required during product lifetime
Characteristic performance (e.g. energy efficiency,
emissions, variation of performance with capacity
utilisation etc.)
Further assumptions for scenario development (e.g.
frequency and time period of use, number of occupants)
None required during product lifetime
None required during product lifetime
End-of-life stage C1-C4
Description of the stage: This stage includes the next modules:
C1, de-construction, demolition;
C2, transport to waste processing;
C3, waste processing for reuse, recovery and/or recycling;
C4, disposal, including provision and a
ll transport, provision of all materials, products and related energy and
water use.
Description of the scenarios and additional technical information for the end-of-life:
PARAMETER
Collection process specified by type
Recovery system specified by type
Disposal specified by type
Assumptions for scenario development (e.g.
transportation)
VALUE (expressed per declared unit)
1.18 kg collected with mixed construction waste
0% of waste
100% (1.18 kg) of plaster to municipal landfill
On average, plaster waste is transported 50 km by truck from
construction/demolition sites to treatment plant (landfill).
Reuse/recovery/recycling potential, D
Description of the stage: module D has not been taken into account.
8
LCA result
Description of the system boundary (X = Included in LCA, MNA = Module Not Assessed)
CML 2001 has been used as the impact model. Specific data has been supplied by the plant, and generic data
come from GABI and Ecoinvent databases.
All emissions to air, water, and soil, a
nd all materials and energy used have been included.
All figures refer to a declared unit of 1 kg of Rigips plaster delivered in powder.
CONSTRUCTION
STAGE
END OF LIFE
STAGE
Transport
Manufacturing
Transport
Construction-Installation
process
Use
Maintenance
Repair
Replacement
Refurbishment
Operational energy use
Operational water use
De-construction
demolition
Transport
Waste processing
Disposal
Reuse-recovery
USE STAGE
Raw material supply
PRODUCT
STAGE
BENEFITS
AND LOADS
BEYOND THE
SYSTEM
BOUNDARY
A1
A2
A3
A4
A5
B1
B2
B3
B4
B5
B6
B7
C1
C2
C3
C4
D
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
MNA
9
B1
Use
B2
Maintenance
B3 Repair
B4
Replacement
B5
Refurbishment
B6
Operational
energy use
B7
Operational
water use
C1
Deconstructio
n / demolition
C2
Transport
C3
Waste
processing
C4
Disposal
End-of-life stage
A5
Installation
Global Warming Potential
(GWP 100) - kg CO2 equiv/FU
Use stage
A4
Transport
Parameters
Construction
proces
s stage
A1 / A2 / A3
Product
stage
1,6E-01
3,4E-02
1,5E-02
0
0
0
0
0
0
0
5,2E-03
2,8E-03
0
1,9E-02
D Reuse, recovery,
recycling
ENVIRONMENTAL IMPACTS
MNA
0
1,8E-14
MNA
The global warming potential of a gas refers to the total contribution to global warming resulting from the emission
of one unit of that gas relative to one unit of the reference gas, carbon dioxide, which is assigned a value of 1.
4,5E-09
4,0E-15
2,3E-10
0
0
0
0
0
0
0
1,4E-15
2,2E-15
Ozone Depletion (ODP)
Destruction of the stratospheric ozone layer which shields the earth from ultraviolet radiation harmful to life.
This destruction of ozone is caused by the breakdown of certain chlorine and/or bromine containing compounds (chlorofluorocarbonsor halons),
which break down when they reach the stratosphere and then catalytically destroy ozone molecules.
kg CFC 11 equiv/FU
Acidification potential (AP)
5,2E-04
kg SO2 equiv/FU
Eutrophication potential (EP)
3,1E-04
8,2E-05
0
0
0
0
s stage
A1 / A2 / A3
Product
stage
1,6E-01
3,4E-02
1,5E-02
0
0
0
0
0
0
0
5,2E-03
2,8E-03
0
1,9E-02
D Reuse, recovery,
recycling
ENVIRONMENTAL IMPACTS
MNA
0
1,8E-14
MNA
The global warming potential of a gas refers to the total contribution to global warming resulting from the emission
of one unit of that gas relative to one unit of the reference gas, carbon dioxide, which is assigned a value of 1.
4,5E-09
4,0E-15
2,3E-10
0
0
0
0
0
0
0
1,4E-15
2,2E-15
Ozone Depletion (ODP)
Destruction of the stratospheric ozone layer which shields the earth from ultraviolet radiation harmful to life.
This destruction of ozone is caused by the breakdown of certain chlorine and/or bromine containing compounds (chlorofluorocarbonsor halons),
which break down when they reach the stratosphere and then catalytically destroy ozone molecules.
kg CFC 11 equiv/FU
Acidification potential (AP)
5,2E-04
kg SO2 equiv/FU
Eutrophication potential (EP)
3,1E-04
8,2E-05
0
0
0
0
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