Sustainability of construction works - Environmental product declarations - Core rules for road materials - Part 1: Bituminous mixtures

This document provides core product category rules for type III environmental declaration of bituminous materials for building and civil engineering according to EN 13108-1, EN 13108-2, EN 13108-3, EN 13108-4, EN 13108-5, EN 13108-6, EN 13108-7, EN 13108-9, and prEN 13108-31. The approach taken for these PCR may be considered applicable and adaptable for other bitumen based products.
This document defines the parameters to be reported, what EPD types (and life cycle stages) to be covered, what rules to be followed in order to generate Life Cycle Inventories (LCI) and conduct Life Cycle Impact Assessment (LCIA) and the data quality to be used in the development of EPDs.
In addition to the common parts of EN 15804, this document for bituminous materials:
-   defines the system boundaries;
-   defines the modelling and assessment of material-specific characteristics;
-   defines allocation procedures for multi-output processes along the production chain;
-   includes the rules for calculating the LCI and the LCIA underlying the EPD;
-   provides guidance for the determination of the reference service life (RSL);
-   gives guidance on the establishment of default scenarios.
Principles used:
-   PCR covering bituminous materials;
-   from cradle to beyond the building life cycle based on EN 15804;
-   polluter pays: processes of waste processing shall be assigned to the product system that generates the waste until the end-of-waste state is reached;
-   EPD will be based on declared units (e.g. tonnes of material) and not functional units (e.g. km of road);
-   abiotic depletion potential of aggregate should be declared when relevant;
-   all use of inert material in the quarry: reclamation, sound and dust protection have to be included in stages A1 to A3 of the EPD;
-   data quality will be described (e.g. Average yearly value, average 10 years value, or maximum value ever encountered).
NOTE   The Use stage, Informative Module B, depends on the use scenario and this depends on the type of road it is used for, the width of the road, the width of the lane, the total pavement structure and substrate for which the pavement layer it is used, the climate conditions, the maximum and minimum pavement temperatures, the traffic intensity and the number of weights of the axle loadings, etc. The use scenario details are determined by the buyer / user of the bituminous mixture. Therefore, only examples on typical maintenance scenarios are given.
This guideline provides PCRs that can be applied for a particular asphalt mixture, from a specific asphalt plant with a specific production temperature. Hence, the design of the asphalt mixture is necessary to produce the specific EPD.

Nachhaltigkeit von Bauwerken - Umweltproduktdeklarationen - Festlegungen für Straßenbaustoffe - Teil 1: Asphaltmischgut

Dieses Dokument liefert grundlegende Produktkategorieregeln für Typ III Umweltdeklarationen für bitumenhaltige Materialien im Bauwesen nach EN 13108 1, EN 13108 2, EN 13108 3, EN 13108 4, EN 13108 5, EN 13108 6, EN 13108 7, EN 13108 9 und EN 13108 31. Der für diese PCR gewählte Ansatz kann als anwendbar und anpassbar für andere auf Bitumen basierende Produkte betrachtet werden.
Dieses Dokument definiert die anzugebenden Parameter, die abzudeckenden EPD Typen (und Lebens-zyklusphasen), die Regeln, die eingehalten werden müssen, um Sachbilanzen (LCI, en: life cycle inventory) zu erstellen und Wirkungsabschätzungen (LCIA, en: life cycle impact assessment) durchzuführen, und die zu verwendende Datenqualität bei der Entwicklung von EPD.
Zusätzlich zu den gemeinsamen Teilen der EN 15804 liefert dieses Dokument für bitumenhaltige Materialien Folgendes:
—   die Definition der Systemgrenzen;
—   die Definition von Modellierung und Bewertung materialspezifischer Merkmale;
—   die Definition von Allokationsverfahren für Multi-Output-Prozesse entlang der Produktionskette;
—   Berechnungsregeln für die der EPD zugrunde liegenden LCI und LCIA;
—   eine Anleitung zur Bestimmung der Referenz-Nutzungsdauer (RSL, en: reference service life);
—   eine Anleitung zur Festlegung von Standardszenarien.
Angewandte Prinzipien:
—   PCR deckt bitumenhaltige Materialien ab;
—   von „der Wiege“ über den Lebenszyklus des Gebäudes hinaus, auf der Grundlage von EN 15804;
—   Verursacher zahlt: Prozesse zur Abfallbehandlung müssen dem Produktsystem zugeordnet werden, welches den Abfall erzeugt, bis der Status „Abfallende“ (en: end of waste) erreicht ist;
—   EPD basieren auf deklarierten Einheiten (z. B. Material in Tonnen) und nicht auf funktionellen Einheiten (z. B Straßenlänge in km);
—   abiotisches Abbaupotential von Gesteinskörnung sollte gegebenenfalls deklariert werden;
—   gesamte Nutzung von inertem Material im Steinbruch: Rückgewinnung, Schall- und Staubschutz müssen in die EPD Phasen A1 bis A3 aufgenommen werden;
—   Beschreibung der Datenqualität (z. B.: durchschnittlicher Jahreswert, durchschnittlicher Wert über einen Zeitraum von 10 Jahren oder der jemals vorgefundene Höchstwert).
ANMERKUNG   Die Nutzungsphase, Informationsmodul B, hängt vom Nutzungsszenario ab, welches wiederum ab-hängig ist vom Straßentyp, für das es verwendet wird, von der Straßenbreite, der Fahrspurbreite, der gesamten Struktur und Oberfläche der für den Fahrbahnbelag verwendeten Beschichtung, den Klimabedingungen, den Höchst- und Tiefsttemperaturen des Belags, der Verkehrsdichte, der Anzahl der Gewichte der Achslasten usw. Die Details des Nutzungsszenarios werden vom Käufer/Anwender des Asphaltmischguts bestimmt. Aus diesem Grund werden nur Bei¬spiele für typische Instandhaltungsszenarien gegeben.
Dieser Leitfaden liefert PCR, die auf ein bestimmtes Asphaltmischgut eines spezifischen Asphaltwerks mit einer bestimmten Produktionstemperatur angewandt werden können. Deshalb ist die Auslegung des Asphaltmischguts zur Erstellung der spezifischen EPD notwendig.

Contribution des ouvrages de construction au développement durable - Déclarations environnementales sur les produits - Règles régissant les matériaux de structure de chaussée - Partie 1 : mélanges bitumineux

Le présent document fournit des règles de définition des catégories de produits destinées aux déclarations environnementales de type III de matériaux bitumineux pour la construction et le génie civil conformément à l’EN 13108 1, l’EN 13108 2, l’EN 13108 3, l’EN 13108 4, l’EN 13108 5, l’EN 13108 6, l’EN 13108 7, l’EN 13108 9, et l’EN 13108 31. La démarche adoptée pour ces RDCP peut être considérée comme applicable et adaptable à d’autres produits à base de bitume.
Le présent document définit les paramètres à consigner, les types de DEP (et phases du cycle de vie) à couvrir, les règles à suivre afin de créer des inventaires du cycle de vie (ICV) et de réaliser des évaluations de l’impact du cycle de vie (EICV) ainsi que la qualité des données à respecter dans le cadre du développement des DEP.
Outre les parties communes de l’EN 15804, le présent document consacré aux matériaux bitumineux :
- définit les frontières du système ;
- définit la modélisation et l’évaluation des caractéristiques spécifiques au matériau ;
- définit les modes opératoires d’allocation pour les processus à multiples extrants le long de la chaîne de production ;
- intègre les règles de calcul de l’ICV et de l’EICV sous-jacents aux DEP ;
- fournit des indications pour la détermination de la durée de vie documentée (DVD) ;
- fournit des indications sur l’établissement de scénarios par défaut.
Principes exploités :
- RDCP couvrant les matériaux bitumineux ;
- du berceau au-delà du cycle de vie de construction sur la base de l’EN 15804 ;
- principe pollueur-payeur : les processus de traitement des déchets doivent être affectés au système de produit générant le déchet jusqu’à ce que l’état de fin du déchet soit atteint ;
- la DEP sera basée sur les unités déclarées (par ex. tonnes de matériau) et non les unités fonctionnelles (par ex. km de route) ;
- il convient que le potentiel d’appauvrissement abiotique des granulats soit déclaré le cas échéant ;
- tout usage de matériaux inertes en carrière : la réhabilitation et la protection contre le bruit et la poussière doivent être incluses dans les phases A1 à A3 de la DEP ;
- la qualité des données sera décrite (par ex. valeur moyenne annuelle, valeur moyenne à 10 ans, ou valeur maximale historique).
NOTE La phase d’utilisation, module informatif B, dépend du scénario d’utilisation et ce dernier dépend du type de route pour lequel il est utilisé, de la largeur de la route, de la largeur de la voie, de la structure totale de la chaussée et du substrat destiné à la couche de chaussée pour laquelle il est utilisé, des conditions climatiques, des températures minimale et maximale de la chaussée, de l’intensité de trafic et du nombre de poids de charge à l’essieu, etc. Les informations sur le scénario d’utilisation sont déterminées par l’acheteur/l’utilisateur du mélange bitumineux. Par conséquent, seuls des exemples de scénarios de maintenance typiques sont donnés ;
Le présent guide fournit des RDCP pouvant être appliquées pour un mélange d’asphalte particulier, issu d’une centrale d’enrobage particulière employant une température de production spécifique. La conception du mélange d’asphalte est ainsi nécessaire pour produire la DEP spécifique.

Trajnostnost gradbenih objektov - Okoljske deklaracije za proizvode - Skupna pravila za materiale za ceste - 1. del: Bitumenske zmesi

General Information

Status
Not Published
Publication Date
15-Aug-2021
Withdrawal Date
15-Feb-2022
Technical Committee
CEN/TC 227 - Road materials
Current Stage
4098 - Decision to abandon - Enquiry
Start Date
22-Dec-2020
Completion Date
14-Apr-2025

Overview

The prEN 17392-1 standard, developed by CEN, establishes core product category rules (PCR) for Type III Environmental Product Declarations (EPDs) specifically tailored to bituminous mixtures used in road construction and civil engineering. This standard complements the general framework provided by EN 15804 by focusing on the life cycle assessment (LCA) and environmental impact reporting of bituminous road materials. It aims to ensure consistency, transparency, and comparability in environmental data for asphalt mixtures, facilitating sustainable construction decisions based on scientifically verified information.

Key Topics

  • Scope and Applicability:
    prEN 17392-1 covers bituminous mixtures as defined by various EN 13108 standards (Parts 1 through 9 and 31), including asphalt concrete, soft asphalt, mastic asphalt, porous asphalt, reclaimed asphalt, and others. It is designed for use across roads, airfields, and trafficked surfaces, providing PCR adaptable to other bitumen-based products.

  • Environmental Product Declarations (EPDs):
    This document defines parameters for EPD preparation, focusing on the key environmental indicators derived from Life Cycle Inventory (LCI) and Life Cycle Impact Assessment (LCIA). EPDs developed following this standard are based on declared units (e.g., tonnes of material), not functional units, enhancing transparency.

  • Life Cycle Assessment (LCA) Methodology:
    Core to the document are instructions to:

    • Define system boundaries from cradle to beyond building life cycle (aligned with EN 15804).
    • Model material-specific behaviors and allocate impacts in multi-output processes.
    • Calculate LCI and LCIA data to underpin the environmental declarations.
    • Incorporate waste management impacts with a polluter-pays principle up to end-of-waste state.
  • Reference Service Life (RSL) and Scenario Guidance:
    Guidance is provided for determining RSL of bituminous mixtures, supporting realistic assumptions about in-use performance. Default maintenance and use scenarios are described; however, specifics depend on variables such as road type, traffic intensity, climate, and pavement structure.

  • Data Quality and Reporting:
    The standard mandates description of data quality, such as average yearly or 10-year values, ensuring reliable LCA results. It also requires inclusion of abiotic depletion potential for aggregates and considers quarry inert material handling.

  • Alignment with Existing Standards:
    prEN 17392-1 builds on EN 15804 and ISO 21930 in the environmental sustainability framework, while harmonizing with product specifications from EN 13108 series for bituminous mixtures.

Applications

The prEN 17392-1 standard is critical for manufacturers, suppliers, and specifiers in the road construction sector who wish to quantify and communicate the environmental impacts of their asphalt products. Key applications include:

  • Sustainable Road Design:
    Enabling designers and engineers to integrate verified environmental data when selecting bituminous materials for pavements, promoting greener infrastructure with reduced carbon footprints.

  • Product Environmental Transparency:
    Assisting asphalt producers to develop transparent EPDs that support market-driven environmental improvements and compliance with environmental procurement policies.

  • Life Cycle Performance Analysis:
    Providing a standardized method to assess environmental impacts from raw material extraction, manufacturing, transport, use, maintenance, and end-of-life processes.

  • Regulatory and Market Compliance:
    Facilitating adherence to European construction product sustainability regulations and supporting clients’ decisions in public or private roadworks tenders focused on environmental performance.

Related Standards

  • EN 15804:2012+A2:2019 – Core rules for environmental product declarations of construction products, setting the overarching framework for sustainability assessments.
  • EN 13108 Series – Material specifications for various types of bituminous mixtures, detailing compositional and production requirements.
  • ISO 21930:2017 – Core rules for environmental product declarations in buildings and civil engineering, guiding EPD principles.
  • EN 15978:2011 – Assessment of environmental performance of buildings, complementing PCR for construction materials.
  • Additional related standards include EN 12591, EN 14023, EN 13924 series for bitumen types used in mixtures, and EN 13043 for aggregate specifications.

Keywords: Environmental Product Declarations, EPD, bituminous mixtures, road materials, sustainability, Life Cycle Assessment, LCA, Life Cycle Inventory, LCIA, PCR, prEN 17392-1, EN 15804, asphalt, sustainable construction, road construction materials, environmental impact, reference service life, reclaimed asphalt, bitumen, ISO 21930.

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prEN 17392-1:2020 - BARVE

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Frequently Asked Questions

prEN 17392-1 is a draft published by the European Committee for Standardization (CEN). Its full title is "Sustainability of construction works - Environmental product declarations - Core rules for road materials - Part 1: Bituminous mixtures". This standard covers: This document provides core product category rules for type III environmental declaration of bituminous materials for building and civil engineering according to EN 13108-1, EN 13108-2, EN 13108-3, EN 13108-4, EN 13108-5, EN 13108-6, EN 13108-7, EN 13108-9, and prEN 13108-31. The approach taken for these PCR may be considered applicable and adaptable for other bitumen based products. This document defines the parameters to be reported, what EPD types (and life cycle stages) to be covered, what rules to be followed in order to generate Life Cycle Inventories (LCI) and conduct Life Cycle Impact Assessment (LCIA) and the data quality to be used in the development of EPDs. In addition to the common parts of EN 15804, this document for bituminous materials: - defines the system boundaries; - defines the modelling and assessment of material-specific characteristics; - defines allocation procedures for multi-output processes along the production chain; - includes the rules for calculating the LCI and the LCIA underlying the EPD; - provides guidance for the determination of the reference service life (RSL); - gives guidance on the establishment of default scenarios. Principles used: - PCR covering bituminous materials; - from cradle to beyond the building life cycle based on EN 15804; - polluter pays: processes of waste processing shall be assigned to the product system that generates the waste until the end-of-waste state is reached; - EPD will be based on declared units (e.g. tonnes of material) and not functional units (e.g. km of road); - abiotic depletion potential of aggregate should be declared when relevant; - all use of inert material in the quarry: reclamation, sound and dust protection have to be included in stages A1 to A3 of the EPD; - data quality will be described (e.g. Average yearly value, average 10 years value, or maximum value ever encountered). NOTE The Use stage, Informative Module B, depends on the use scenario and this depends on the type of road it is used for, the width of the road, the width of the lane, the total pavement structure and substrate for which the pavement layer it is used, the climate conditions, the maximum and minimum pavement temperatures, the traffic intensity and the number of weights of the axle loadings, etc. The use scenario details are determined by the buyer / user of the bituminous mixture. Therefore, only examples on typical maintenance scenarios are given. This guideline provides PCRs that can be applied for a particular asphalt mixture, from a specific asphalt plant with a specific production temperature. Hence, the design of the asphalt mixture is necessary to produce the specific EPD.

This document provides core product category rules for type III environmental declaration of bituminous materials for building and civil engineering according to EN 13108-1, EN 13108-2, EN 13108-3, EN 13108-4, EN 13108-5, EN 13108-6, EN 13108-7, EN 13108-9, and prEN 13108-31. The approach taken for these PCR may be considered applicable and adaptable for other bitumen based products. This document defines the parameters to be reported, what EPD types (and life cycle stages) to be covered, what rules to be followed in order to generate Life Cycle Inventories (LCI) and conduct Life Cycle Impact Assessment (LCIA) and the data quality to be used in the development of EPDs. In addition to the common parts of EN 15804, this document for bituminous materials: - defines the system boundaries; - defines the modelling and assessment of material-specific characteristics; - defines allocation procedures for multi-output processes along the production chain; - includes the rules for calculating the LCI and the LCIA underlying the EPD; - provides guidance for the determination of the reference service life (RSL); - gives guidance on the establishment of default scenarios. Principles used: - PCR covering bituminous materials; - from cradle to beyond the building life cycle based on EN 15804; - polluter pays: processes of waste processing shall be assigned to the product system that generates the waste until the end-of-waste state is reached; - EPD will be based on declared units (e.g. tonnes of material) and not functional units (e.g. km of road); - abiotic depletion potential of aggregate should be declared when relevant; - all use of inert material in the quarry: reclamation, sound and dust protection have to be included in stages A1 to A3 of the EPD; - data quality will be described (e.g. Average yearly value, average 10 years value, or maximum value ever encountered). NOTE The Use stage, Informative Module B, depends on the use scenario and this depends on the type of road it is used for, the width of the road, the width of the lane, the total pavement structure and substrate for which the pavement layer it is used, the climate conditions, the maximum and minimum pavement temperatures, the traffic intensity and the number of weights of the axle loadings, etc. The use scenario details are determined by the buyer / user of the bituminous mixture. Therefore, only examples on typical maintenance scenarios are given. This guideline provides PCRs that can be applied for a particular asphalt mixture, from a specific asphalt plant with a specific production temperature. Hence, the design of the asphalt mixture is necessary to produce the specific EPD.

prEN 17392-1 is classified under the following ICS (International Classification for Standards) categories: 91.100.01 - Construction materials in general; 93.080.20 - Road construction materials. The ICS classification helps identify the subject area and facilitates finding related standards.

You can purchase prEN 17392-1 directly from iTeh Standards. The document is available in PDF format and is delivered instantly after payment. Add the standard to your cart and complete the secure checkout process. iTeh Standards is an authorized distributor of CEN standards.

Standards Content (Sample)


SLOVENSKI STANDARD
01-maj-2020
Trajnostnost gradbenih objektov - Okoljske deklaracije za proizvode - Skupna
pravila za materiale za ceste - 1. del: Bitumenske zmesi
Sustainability of construction works - Environmental product declarations - Core rules for
road materials - Part 1: Bituminous mixtures
Nachhaltigkeit von Bauwerken - Umweltproduktdeklarationen - Festlegungen für
Straßenbaustoffe - Teil 1: Asphaltmischgut
Ta slovenski standard je istoveten z: prEN 17392-1
ICS:
13.020.20 Okoljska ekonomija. Environmental economics.
Trajnostnost Sustainability
93.080.20 Materiali za gradnjo cest Road construction materials
2003-01.Slovenski inštitut za standardizacijo. Razmnoževanje celote ali delov tega standarda ni dovoljeno.

DRAFT
EUROPEAN STANDARD
NORME EUROPÉENNE
EUROPÄISCHE NORM
March 2020
ICS 91.100.01; 93.080.20
English Version
Sustainability of construction works - Environmental
product declarations - Core rules for road materials –
Part 1: Bituminous mixtures
Nachhaltigkeit von Bauwerken -
Umweltproduktdeklarationen - Festlegungen für
Straßenbaustoffe - Teil 1: Asphaltmischgut
This draft European Standard is submitted to CEN members for enquiry. It has been drawn up by the Technical Committee
CEN/TC 227.
If this draft becomes a European Standard, CEN members are bound to comply with the CEN/CENELEC Internal Regulations
which stipulate the conditions for giving this European Standard the status of a national standard without any alteration.

This draft European Standard was established by CEN in three official versions (English, French, German). A version in any other
language made by translation under the responsibility of a CEN member into its own language and notified to the CEN-CENELEC
Management Centre has the same status as the official versions.

CEN members are the national standards bodies of Austria, Belgium, Bulgaria, Croatia, Cyprus, Czech Republic, Denmark, Estonia,
Finland, France, Germany, Greece, Hungary, Iceland, Ireland, Italy, Latvia, Lithuania, Luxembourg, Malta, Netherlands, Norway,
Poland, Portugal, Republic of North Macedonia, Romania, Serbia, Slovakia, Slovenia, Spain, Sweden, Switzerland, Turkey and
United Kingdom.
Recipients of this draft are invited to submit, with their comments, notification of any relevant patent rights of which they are
aware and to provide supporting documentation.

Warning : This document is not a European Standard. It is distributed for review and comments. It is subject to change without
notice and shall not be referred to as a European Standard.

EUROPEAN COMMITTEE FOR STANDARDIZATION
COMITÉ EUROPÉEN DE NORMALISATIO N

EUROPÄISCHES KOMITEE FÜR NORMUN G

CEN-CENELEC Management Centre: Rue de la Science 23, B-1040 Brussels
© 2020 CEN All rights of exploitation in any form and by any means reserved Ref. No. prEN 17392-1:2020 E
worldwide for CEN national Members.

Contents Page
European foreword . 3
Introduction . 4
1 Scope . 5
2 Normative references . 6
3 Terms and definitions . 6
4 Abbreviations . 8
5 General aspects . 8
5.1 Objective of the PCR . 8
5.2 Types of EPD with respect to life cycle stages covered . 9
5.3 Comparability of EPD of construction products . 9
5.4 Additional environmental information . 10
5.5 Ownership, responsibility and liability for the EPD. 10
5.6 Communication formats . 10
6 Product category rules for LCA . 10
6.1 Product category . 10
6.2 Life cycle stages and their information modules to be included . 10
6.3 Calculation rules for the LCA . 12
6.4 Inventory analysis . 23
6.5 Impact assessment . 25
7 Content of the EPD . 26
7.1 Declaration of general information. 26
7.2 Declaration of environmental indicators derived from the LCA . 27
7.3 Scenarios and additional technical information . 32
7.4 Additional information on release of dangerous substances to indoor air, soil and
water during the use stage . 34
8 Project report . 34
9 Verification and validity of an EPD . 34
Annex A (normative) Requirements and guidance on the reference service life . 35
Annex B (informative) Waste . 36
Annex C (normative) Impact categories and related indicators, methodologies and
characterization factors (CF) . 37
Annex D (informative) End of life formulae . 40
Bibliography . 41
European foreword
This document (prEN 17392-1:2020) has been prepared by Technical Committee CEN/TC 227 “Road
materials”, the secretariat of which is held by BSI.
This document is currently submitted to the CEN Enquiry.
Introduction
European standard EN 15804 provides Product Category Rules (PCR) for Type III environmental
declarations for any construction product and services.
It provides a structure to ensure that all Environmental Product Declarations (EPD) of construction
products, construction services and construction processes are derived, verified and presented in a
harmonized way.
This document provides additional rules for Environmental Product Declarations (EPD) specifically for
bituminous mixtures. It complements the core product category rules for all construction products and
services as established in EN 15804.
An EPD communicates verifiable, accurate, non-misleading environmental information for products and
their applications, thereby supporting scientifically based, fair choices and stimulating the potential for
market-driven continuous environmental improvement.
The standardization process has taken place in accordance with ISO 14025. All common issues are
covered horizontally for all product types in order to minimize vertical (branch specific) deviations.
All common issues are covered horizontally for all bituminous mixtures in order to minimize intra-
sectoral deviations.
EPD information is expressed in information modules as defined in EN 15804, which allow easy
organization and expression of data packages throughout the life cycle of bituminous mixtures. The
approach requires that the underlying data should be consistent, reproducible and comparable.
In line with EN 15804, the EPD is expressed in a form that allows aggregation (addition) to provide
complete information for construction works. This document does not deal with aggregation at the
construction level nor does this document describe the rules for applying EPD in a construction
assessment.
The document deals with a limited number of quantifiable parameters as predefined in EN 15804.
Future revisions of EN 15804 may lead to the incorporation in this document of additional
predetermined parameters.
NOTE Producers and users of EPDs need to be aware that as each product sector develops its own EPDs,
under their own PCR, then it is generally not possible to compare the outputs of different products or product
types e.g. EPDs for asphalt concrete and surface dressing cannot be directly compared. Comparison between EPDs
can only be realized between mixes that are used in the same application and provide the same performance.
1 Scope
This document provides core product category rules for type III environmental declaration of
bituminous materials for building and civil engineering according to EN 13108-1, EN 13108-2,
EN 13108-3, EN 13108-4, EN 13108-5, EN 13108-6, EN 13108-7, EN 13108-9, and EN 13108-31. The
approach taken for these PCR may be considered applicable and adaptable for other bitumen based
products.
This document defines the parameters to be reported, what EPD types (and life cycle stages) to be
covered, what rules to be followed in order to generate Life Cycle Inventories (LCI) and conduct Life
Cycle Impact Assessment (LCIA) and the data quality to be used in the development of EPDs.
In addition to the common parts of EN 15804, this document for bituminous materials:
— defines the system boundaries;
— defines the modelling and assessment of material-specific characteristics;
— defines allocation procedures for multi-output processes along the production chain;
— includes the rules for calculating the LCI and the LCIA underlying the EPD;
— provides guidance for the determination of the reference service life (RSL);
— gives guidance on the establishment of default scenarios.
Principles used:
— PCR covering bituminous materials;
— from cradle to beyond the building life cycle based on EN 15804;
— polluter pays: processes of waste processing shall be assigned to the product system that generates
the waste until the end-of-waste state is reached;
— EPD will be based on declared units (e.g. tonnes of material) and not functional units (e.g. km of
road);
— abiotic depletion potential of aggregate should be declared when relevant;
— all use of inert material in the quarry: reclamation, sound and dust protection shall be included in
stages A1 to A3 of the EPD;
— data quality will be described (e.g. Average yearly value, average 10 years value, or maximum value
ever encountered).
NOTE The Use stage, Informative Module B, depends on the use scenario and this depends on the type of road
it is used for, the width of the road, the width of the lane, the total pavement structure and substrate for which
pavement layer it is used, the climate conditions, the maximum and minimum pavement temperatures, the traffic
intensity and the number of weights of the axle loadings, etc. The use scenario details are determined by the buyer
/ user of the bituminous mixture. Therefore, only examples on typical maintenance scenarios are given.
This guideline provides PCRs that can be applied for a particular asphalt mixture, from a specific asphalt
plant with a specific production temperature. Hence, the design of the asphalt mixture is necessary to
produce the specific EPD.
2 Normative references
The following documents are referred to in the text in such a way that some or all of their content
constitutes requirements of this document. For dated references, only the edition cited applies. For
undated references, the latest edition of the referenced document (including any amendments) applies.
EN 15804:2012+A2:2019, Sustainability of construction works — Environmental product declarations —
Core rules for the product category of construction products
EN 15978:2011, Sustainability of construction works - Assessment of environmental performance of
buildings - Calculation method
ISO 21930, Sustainability in buildings and civil engineering works — Core rules for environmental product
declarations of construction products and services
EN 13108-1, Bituminous mixtures - Material specifications – Part 1: Asphalt Concrete
EN 13108-2, Bituminous mixtures - Material specifications – Part 2: Asphalt Concrete for Very Thin Layers
(BBTM)
EN 13108-3, Bituminous mixtures - Material specifications – Part 3: Soft Asphalt
EN 13108-4, Bituminous mixtures - Material specifications – Part 4: Hot Rolled Asphalt
EN 13108-5, Bituminous mixtures - Material specifications – Part 5: Stone Mastic Asphalt
EN 13108-6, Bituminous mixtures - Material specifications – Part 6: Mastic Asphalt
EN 13108-7, Bituminous mixtures - Material specifications – Part 7: Porous Asphalt
EN 13108-8, Bituminous mixtures - Material specifications – Part 8: Reclaimed Asphalt
EN 13108-9, Bituminous mixtures - Material specifications – Part 9: Asphalt for Ultra-Thin Layer (AUTL)
EN 13108-31, Bituminous mixtures — Material specifications — Part 31: Asphalt Concrete with
Bituminous Emulsion (ACBE)
3 Terms and definitions
For the purposes of this document, the terms and definitions given in EN 15804 and the following apply.
ISO and IEC maintain terminological databases for use in standardization at the following addresses:
— IEC Electropedia: available at http://www.electropedia.org/
— ISO Online browsing platform: available at https://www.iso.org/obp
3.1
aggregate
granular material used in construction
Note to entry 1: Aggregate maybe natural, manufactured or recycled (see EN 13043).
3.2
asphalt mixture
homogenous mixture typically of coarse and fine aggregates, filler aggregate, bituminous binder, and
additives which is used in the construction of a pavement
Note to entry 1: They are plant produced materials in accordance with EN 13108 series of European standards.
Note to entry 2: The mixture may contain reclaimed asphalt or chemical additives or organic additives or pigment
or fibre or combination of these to replace partially or completely some components.
3.3
bituminous binder
liquid residue obtained from the distillation of suitable crude oils or derived from naturally occurring
deposits
Note to entry 1: Shall be a paving grade bitumen, a polymer modified bitumen, a hard paving
grade bitumen, a multigrade bitumen or a blend of one of them with natural asphalt.
Note to entry 2: Relevant European standards are EN 12591 for paving grade bitumen, EN 14023
for polymer modified bitumen, EN 13924-1 for hard paving grade bitumen, and EN 13924-2 for
multigrade bitumen.
3.4
environmental product declaration
EPD
environmental declaration providing quantified environmental data using predetermined parameters
and, where relevant, additional environmental information
[SOURCE: ISO 21930]
3.5
estimated service life
ESL
service life that a building or an assembled system (part of works) would be expected to have in a set of
specific in-use conditions, determined from reference service life data after taking into account any
differences from the reference in use conditions
[SOURCE: EN 15978:2011]
3.6
mixture additives
used to enhance the laying characteristics, performance or appearance of the mixture
3.7
reclaimed asphalt
RA
processed site-won asphalt, suitable and ready to be used as constituent material for asphalt, after
being tested, assessed and classified
[SOURCE: EN 13108-8]
3.8
site-won asphalt
material to be recycled, in the form of milled asphalt road layers or as slabs ripped up from asphalt
pavements, or being asphalt from reject, surplus or failing production
4 Abbreviations
For the purposes of this document, the following abbreviations apply.
AP Acidification Potential
ADP Abiotic Depletion Potential
DU Declared Unit
EP Eutrophication Potential
EPD Environmental Product Declaration
ESL Estimated Service Life
FU Functional Unit
GWP Global Warming Potential
LCA Life Cycle Assessment
LCI Life Cycle Inventory analysis
LCIA Life Cycle Impact Assessment
ODP Ozone Depletion Potential
PCR Product Category Rules
POCP Photochemical Ozone Creation Potential
RA Reclaimed Asphalt
RSL Reference Service Life
SVHC Substance of Very High Concern
REACH Registration, Evaluation, Authorization and Restriction of Chemicals
5 General aspects
5.1 Objective of the PCR
In addition to the text in EN 15804:
The objective of this document is to provide rules for bituminous materials for use on roads, airfields
and other trafficked areas.
5.2 Types of EPD with respect to life cycle stages covered

Figure 1 — Types of EPD with respect to life cycle stages covered and life cycle stages and
modules for the building assessment
5.3 Comparability of EPD of construction products
In addition to the text in EN 15804:
In principle the comparison of products on the basis of their EPD is defined by the contribution they
make to the environmental performance of the construction works. Consequently comparison of the
environmental performance of construction products using the EPD information shall be based on the
product’s use in and its impacts on the construction, and shall consider the complete life cycle (all
information modules).
NOTE 1 EPDs in a construction works context are not tools to compare construction products and construction
services.
NOTE 2 For the sustainability assessment of construction works comparisons of the environmental aspects and
impacts need to be undertaken in conjunction with the social and economic aspects and impacts related to the
construction works.
NOTE 3 For the interpretation of a comparison, benchmarks or reference values are needed. This document
does not set benchmarks or reference values.
Comparisons are possible at the sub-element level, e.g. for assembled systems, components, products
for one or more life cycle stages. In such cases the principle that the basis for comparison of the
assessment is the entire construction works, shall be maintained by ensuring that:
— the same functional requirements as defined by legislation or in the client’s brief are met;
— the environmental performance and technical performance of any assembled systems, components,
or products excluded are the same;
— the amounts of any material excluded are the same;
— excluded processes or life cycle stages are the same;
— the influence of the product systems on the operational aspects and impacts of the construction
works are taken into account.
The information provided for such comparison shall be transparent to allow the purchaser or user to
understand the limitations of comparability. A justification shall be given for any excluded aspects.
NOTE 4 The difference between two products may be insignificant in the construction works context.
Where an EPD does not cover all life cycle stages relevant for the comparison, e.g. B1 to B7, or if the
assumptions underlying the scenario of a declared information module are not applicable in the
construction works context, then investigations will be required to determine the environmental
aspects and impacts of specific scenarios for the calculation of modules beyond the cradle to gate
modules. These calculations shall be based on scenarios and conditions that are appropriate for the
construction works as the object of assessment.
5.4 Additional environmental information
EN 15804:2012+A2:2019 shall apply.
5.5 Ownership, responsibility and liability for the EPD
EN 15804:2012+A2:2019 shall apply.
5.6 Communication formats
EN 15804:2012+A2:2019 shall apply.
6 Product category rules for LCA
6.1 Product category
In addition to the text in EN 15804:
The product category referred to in this document includes all bituminous mixtures conforming to
EN 13108-1, EN 13108-2, EN 13108-3, EN 13108-4, EN 13108-5, EN 13108-6, EN 13108-7, EN 13108-9
and EN 13108-31.
6.2 Life cycle stages and their information modules to be included
6.2.1 General
The environmental information of an EPD covering all life cycle stages (“cradle to grave”) is subdivided
into the information module groups A1-A3, A4-A5, B1-B5, B6-B7, C1-C4 and module D.
Only the declaration of the modules, A1-A3, C1-C4 and D is required for compliance with this document,
defined as cradle to gate in EN 15804, A2.
The declaration of modules A4-A5, B1-B7 is optional. B1 to B7 would not normally be included for
bituminous mixtures.
6.2.2 A1-A3 product stage, information modules
In addition to the text of EN 15804:
This document accounts for processes that are within the bounds of phases A1: Raw Material Supply,
A2: Transport and A3: Manufacturing of the product stage (see Figure 2). For phase A1 “Raw Material
Supply” this includes aggregates, bituminous binder, additives, reclaimed asphalt, recycled secondary
materials and water for dust control.
All inputs and outputs to the unit processes identified shall be included in the calculation.

Figure 2 —Diagram of destinations of modular information used for life cycle assessments for
pavements
6.2.3 A4-A5 construction process stage, information modules
In addition to the text of EN 15804:
The inclusion of A4 and A5 (transport and Installation) is allowed and recommended.
6.2.4 B1-B5 use stage
The use stage, related to the asphalt pavement layer includes:
— B1, use of the installed asphalt layer;
— B2, maintenance;
— B3, repair;
Not to be applied. An asphalt layer can be “repaired” by replacing a damaged part. This is covered
under maintenance.
— B4, replacement;
— B5, refurbishment;
Not to be applied. This is covered under replacement.
including provision and transport of all materials, products and related energy and water use, as well as
waste processing up to the end-of-waste state or disposal of final residues during this part of the use
stage. These information modules also include all impacts and aspects related to the losses during this
part of the use stage (i.e. production, transport, and waste processing and disposal of the lost products
and materials). Information on typical maintenance scenarios and RSL shall be given.
6.2.5 B6 B7
Not to be applied (not relevant for bituminous products).
6.2.6 C1-C4 end-of-life stage information modules
Information on typical end of life scenarios shall be given.
NOTE Today new pavements are designed to be 100 % recycled / reused in the future. Therefore 100 % of
bituminous products will be recycled in new pavements at the end of their life.
6.2.7 D benefits and loads beyond the product system boundary (module D)
Information on benefits and load scenarios shall be given.
6.3 Calculation rules for the LCA
6.3.1 Functional or declared unit
Refer to EN 15804:2012+A2:2019.
6.3.2 Functional unit
The functional unit can be defined if module B is used. The functional unit shall be able to be calculated
from the declared unit (see EN 15804:2012+A2:2019, 6.3.2.1).
6.3.3 Declared unit
One metric tonne of bituminous mixture.
6.3.4 Reference service life (RSL)
In addition to the text in EN 15804:
Information on RSL shall be given.
The reference service life of the bituminous product shall be consistent with the period of evaluation of
the Civil Engineering Works.
The technical service life of bituminous mixtures is often determined by the practical service life
because of changing the layout of the road infrastructure. The technical service life of bituminous
pavement layers depends on the bearing capacity of the substrate, the conditions of the lower
bituminous layers, the traffic loadings, etc.
6.3.5 System boundaries
6.3.5.1 General
In addition to the text in EN 15804:

Figure 3 — Diagram of the system boundaries, processes, and data types
6.3.5.2 Product stage
In addition to the text in EN 15804:
— Processes in phase A1: Raw Material Supply
Data for all these processes will be based on secondary data, supplier data sources and/or existing
national LCI data. Transportation distances that are part of upstream processes, involving transport of a
raw material through the supply chain before it arrives to the plant, are considered part of the
secondary data. The following impacts are included:
a) Impacts of all co-products of crude oil refining including extraction, transport, refining, and storage.
The co-products of interest to this PCR guidance include gasoline, diesel, residual fuel oil, polymers,
bitumen additives and bituminous binder. The Eurobitume LCI Methodology is used to allocate the
relative impacts of the crude oil refining process across the different co-products.
b) Impacts associated with the extraction and production of burner fuels.
c) Impacts associated with the mining, extraction and production of aggregate.
d) Impacts associated with the use of asphalt additives (including water for foaming).
e) Impacts associated with the processing of site won asphalt to become RA.
f) Transportation of site-won asphalt to the processing plant, is considered to be zero because it is
part of the previous system supplying recycled aggregate into the current system. The system
boundary is considered to be crossed at the site once the reclaimed asphalt enters the processing
plant and impacts after this point (e.g. crushing and sieving) are considered in this system (see
Figure 4).
g) Impacts associated with the production of electricity and transmission to asphalt plant.

Figure 4 — Reclaimed Asphalt processing model with elementary flows
— Processes in phase A2: Transport to Asphalt Mixing Plant
Transportation distances of raw materials to the plant are considered to be primary data.
a) Transportation of bituminous binders to the asphalt mixing plant.
b) Transportation of aggregate to the asphalt mixing plant.
c) Transportation of asphalt additives to the asphalt plant.
d) Transportation of the burner fuels to the asphalt mixing plant.
e) Transportation of RA from processing unit to asphalt plant.
— Processes in phase A3: Manufacturing
All data collected for this part of the system will be directly based on plant operations and will be
considered primary data.
a) Energy (fuel and electricity) used at the plant for the mix production process including:
1) Vehicles used in moving aggregate and other related mobile equipment used on site for the
production of asphalt mixtures.
2) Burner used for drying and heating of aggregates and RA.
3) Heating of bituminous binder in storage tanks.
4) Movement of materials (belts and conveyors) through the plant and mixing process.
5) Asphalt mixture storage in silos.
6) Asphalt Additive addition completed at the plant.
b) Total amount of water used on the plant for dust control, etc.
c) Total amount of bituminous binder, aggregates, reclaimed asphalt and additives used.
d) Output/emissions from plant:
1) Total plant emissions from stack according to ISO 14025.
2) Waste associated with plant and equipment maintenance activities (e.g. loader tyres,
lubricants, dust filter).
6.3.5.3 Construction stage
— Processes in phase A4: Transportation from the production gate to the construction site
Transportation distance of the asphalt mixture from the production gate to the construction site are
considered to be primary data.
— Processes in phase A5: Installation of the product
All data collected for this part of the system will be directly based on plant operations and will be
considered primary data.
a) Transportation of the paving and compaction equipment to the construction site.
b) Energy (fuel) used by the equipment at the construction site including:
1) Sweepers, including the use of water.
2) Equipment to apply tack or bond coat.
3) Material Transfer Vehicle.
4) Heaters to heat the substrate.
5) Asphalt paver / finisher.
6) Compaction equipment.
7) Other equipment used to be able to apply and compact the bituminous product and except
equipment for traffic management, traffic control, road markings, cutting the grass, etc., which
is not to be included.
c) Total amount of water used to cool the drums of the compaction equipment can be neglected as
they meet the cut-off criteria.
d) Output/Emissions from plant
1) Waste associated with equipment cleaning and maintenance activities (e.g. paver and
compaction equipment lubricants, dust filter) may be included, even if they meet the cut-off
criteria.
6.3.5.4 Use stage
6.3.5.4.1 General
EN 15804:2012+A2:2019 shall apply.
6.3.5.4.2 B1-B5 Use stage information modules
— B1 Use of the installed product in terms of any emissions to the environment (not covered by B2-
B7)
Release of substances from the asphalt pavement to soil or ground water:
The EPD does not need to give this information because the horizontal standards on measurement of
release of regulated dangerous substances from construction products using harmonized test methods
according to the provisions of the respective technical committees for European product standards are
not available yet.
— B2 Maintenance
The module “Maintenance” covers the combination of all planned technical and associated
administrative actions during the service life to maintain the product installed in construction works or
its parts in a state in which it can perform its required functional and technical performance, as well as
preserve the aesthetic qualities of the product.
These minor maintenance activities will include preventative and regular maintenance activity such as
filling cracks, sealing of cracks, minor (pothole) patching and replacement of damaged or degraded
parts (mill and fill).
Next to these minor maintenance activities there are also “major maintenance techniques”, which apply
to the whole surface of the pavement. The mostly used major maintenance techniques are surface
treatment, non-structural asphalt overlay and structural asphalt overlay.
The boundary of “maintenance” shall include in addition:
— the production and transportation of any component and ancillary products used for maintenance,
including cleaning;
— transportation of any waste from maintenance processes or from maintenance related
transportation;
— the end-of-life processes of any waste from transportation and the maintenance process, including
any part of the component and ancillary materials removed.
— B3 repair
Not to be applied. An asphalt layer can be “repaired” by replacing a damaged part. This is covered under
maintenance.
— B4 Replacement
An asphalt top layer or a part of the upper layers or a whole asphalt pavement can be replaced.
The boundary for “replacement” shall include:
— the production of the bituminous mixture used for replacement;
— replacement process, including related water and energy use and the production aspects and
impacts of any waste of materials used during the replacement process;
— the transportation of the bituminous mixture and equipment used for cleaning and replacement;
— the end-of-life processes of the removed bituminous mixture.
— B5 Refurbishment
Not to be applied. This is covered under replacement.
6.3.5.4.3 B6-B7 use stage information modules related to the operation of buildings
— B6 Energy use to operate building integrated technical systems
Not to be applied.
— B7 operational water use by building integrated technical systems
Not to be applied.
6.3.5.5 End-of-life stage
In addition to the text in EN 15804:
Processes in phase C1: Deconstruction of the asphalt pavement layer or asphalt pavement. This
deconstruction can result in asphalt slabs or milled granulated asphalt.
Processes in phase C2: Transportation of the bituminous pavement material as part of the waste
processing, e.g. to a recycling site and transportation of waste e.g. to final disposal;
Processes in phase C3: Reclaimed asphalt processing will take place in phase A1:5 as waste processing
is part of the product system under study. The reclaimed asphalt will be crushed and / or sieved into
size fractions for further reuse or recycling.
6.3.6 Criteria for the exclusion of inputs and outputs
In addition to the text in EN 15804:
a) Upstream impacts of extraction, production, and manufacturing of any material that is not
consumed in the production of the asphalt mixture is considered to be part of the plant
infrastructure and therefore may be excluded from the system boundary.
For example:
1) The asphalt mixture production equipment and machinery and its upkeep and maintenance,
including dust filters, loader tyres, lubricants and any other substance used to facilitate the
smooth functioning of the plant;
2) Machinery for the recycling of site-won asphalt;
3) Solar panels or any other alternative energy apparatus that is used to substitute traditional
energy sources at the plant;
4) General management, office, and headquarter operations;
5) Personnel at the plant or their commuting to and from the plant.
b) In case of insufficient input data or data gaps for a unit process, the cut-off criteria shall be 1 % of
the total (renewable and non-renewable) primary energy usage and 1 % of the total mass input of
that unit process. The total sum of neglected input flows shall not exceed 5 % of energy usage and
mass. This applies particularly to material and energy flows known to have the potential to cause
significant emissions into air and water or soil during the life cycle of the product; it also applies to
processes that are known to be resource intensive.
c) Materials that are less than 1 % of the total mass input but are considered environmentally relevant
include additives and polymers such as those listed below. There are data gaps in their publicly
available life cycle inventories and these materials should be included when publicly available data
exists. This may include, but not limited to, the following:
1) Polymers in binder, broken down into two classes of chemicals: elastomers or rubbers, such as
styrene-butadiene-styrene (SBS), and plastomers.
2) Liquid antistrips, recycling agents, and warm-mix chemical additives.
3) Fibres.
d) Recycled material
All inputs and outputs to a (unit) process shall be included in the calculation, for which data are
available. Data gaps may be filled by conservative assumptions with average or generic data. Any
assumptions for such choices shall be documented. Particular care should be taken to include material
and energy flows known to have the potential to cause significant emissions into air and water or soil
related to the environmental indicators of this standard. Conservative assumptions in combination with
plausibility considerations and expert judgement can be used to demonstrate compliance with these
criteria.
6.3.7 Selection of data
In addition to the text in EN 15804:
An EPD describing an average product shall be calculated using representative average data of the
products declared by the EPD (preferred solution).
An EPD describing a specific product shall be calculated using specific data for at least the processes the
producer of the specific product has influence over. Generic data may be used for the processes the
producer cannot influence e.g. processes dealing with the production of input commodities, e.g. raw
material extraction or electricity generation, often referred to as upstream data (see Table 1)
(alternative solution).
NOTE It is essential to have data which meet EPD objectives, at the stated level (e.g. national, European level)
especially for the following:
Table 1 — Application of generic and specific data
Module A1-A3 A4 and A5 B1-B7 C1-C4
MODULES Production of
Product Installation Use End-of-life
commodities,
manufacture processes processes processes
raw materials
Upstream Downstream Downstream Downstream

processes processes processes processes
Except for the
production of
Scenario Scenario Scenario
raw material
based based based
0/X mm arising
from
•the
Process
deconstruction
type
Processes the
stage that is
manufacturer
already handled
has influence
by the
over
construction or
road product
•the production
stage of the
industrial by-
product (or
material/matte
r which has
ceased to be a
waste) used as
raw material
that is already
handled by the
production
system of the
industrial main
product
Manufacturer’s
Data type Generic data average or Generic data Generic data Generic data
specific data
NOTE  Generic data may be average or specific. Normally it is used to describe upstream and
downstream processes. See CEN/TR 15941, Sustainability of construction works — Environmental
When data from EPDs are used for upstream and downstream processes, the use of an
EN 15804 compliant format for an EPD is preferable.
When available, energy mixes used for EPD are those provided by the suppliers. If not available,
reference databases shall be used.
Data assumption for average EPDs can be defined at national level following principles available in
the place of production and use.
6.3.8 Data quality requirements
The quality of the data used to calculate an EPD shall be addressed in the project report (see Clause 8
and EN ISO 14044:2006, 4.2.3.6). In addition the following specific requirements apply:
a) Age — Data considered, collected and used should be no more than 5 years old, unless it is
unchanged and verified by third party.
b) Representativeness — Data should represent the technology in use.
c) Geography — Data should represent the proper geographical region.
d) Local data when available, and then regional or national data should be used.
e) Alternative data sources modified with the local energy mix may be used.
f) Precision — Data shall be reported to no more than two significant figures.
g) Units —metric units have to be used.
h) Completeness — Shall include all data within the defined system boundaries as noted in this
document.
i) Uncertainty — Shall evaluate any assumptions and primary data through sensitivity analysis as
noted in this standard.
Data sources should be publicly available and freely accessible to ensure transparency. Use of
transparent data source will ensure comparability among EPDs developed using this document by
limiting any variability due to differences in the upstream data within the system boundaries.
6.3.9 Development product scenarios
6.3.9.1 General
Scenarios shall support the calculation of information modules except the modules A1-A3. A scenario
shall be based on relevant technical information.
6.3.9.2 Construction stage
6.3.9.2.1 A4, Transportation from the production gate to the construction site
Scenarios shall consider the most common way to deliver the product from the factory to the site, the
most plausible route and vehicle.
Scenarios shall include:
— fuel type and consumption of vehicle type used for transport the declared unit;
— distance from asphalt plant to construction site;
— capacity utilization according to weight limits, including empty returns (if applicable).
6.3.9.2.2 A5, Installation of the product
Scenarios shall consider the most common ways to install the bituminous mixture. For some
applications additional equipment might be needed like sweepers, tack or bond coat application
equipment, Material Transfer Vehicles and / or heaters to heat the substrate.
Scenarios for installation of bituminous mixture shall include the following:
— water use, if relevant;
— quantitative description of energy type and consumption during the installation process;
— other resource use.
6.3.9.3 Use stage
6.3.9.3.1 Use of the bituminous mixture
There are no environmental impacts related to the normal use of bituminous mixture other than the
potential release of substances. The assessment of those aspects shall be based on scenarios described
for the use stage of the installed product.
6.3.9.3.2 B2, Maintenance
Scenarios for maintenance shall take into account inspection, cleaning (except snow removal) and
specific maintenance operations that may be required.
6.3.9.3.3 B3, Repair
When correctly designed and installed, repair of bituminous mixtures is not relevant.
6.3.9.3.4 B4, Replacement
An asphalt top layer or a part of the upper layers or a whole asphalt pavement can be replaced.
Scenarios for replacement stage B4 shall include the following:
— the production of the bituminous mixture used for replacement;
— replacement process, including related water and energy use and the production aspects and
impacts of any waste of materials used during the replacement process;
— the transportation of the bituminous mixture and equipment used for c
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