ANNEX
EU ECOLABEL CRITERIA AND ASSESSMENT AND VERIFICATION REQUIREMENTS
Criteria for awarding the EU Ecolabel to ‘footwear’:
Origin of hides and skins, cotton, wood and cork, and man-made cellulose fibres;
Reduction of water consumption and restriction on the tanning of hides and skins;
Emissions to water from the production of leather, textiles and rubber;
Hazardous substances in the product and shoe components;
Restricted Substances List (RSL);
Parameters contributing to durability;
Corporate Social Responsibility with regard to labour aspects
Packaging;
Information on the packaging.
Assessment and verification: The detailed assessment and verification requirements are indicated for each criterion.
Where the applicant is required to provide declarations, documentation, analyses, test reports, or other evidence to show compliance with the criteria, these may originate from the applicant or his or her supplier(s) or their suppliers, as appropriate.
Competent bodies shall preferentially recognise attestations which are issued by bodies accredited according to the relevant harmonised standard for testing and calibration laboratories and verifications by bodies that are accredited according to the relevant harmonised standard for bodies certifying products, processes and services.
Where appropriate, test methods other than those indicated for each criterion may be used if the competent body assessing the application accepts their equivalence.
Where appropriate, competent bodies may require supporting documentation and may carry out independent verifications or site visits.
The final product is one pair of shoes. Requirements are based on shoe size: 42 Paris point for men, 38 Paris point for women, 40 Paris point for unisex models, 32 Paris point for children (or the largest size in the case of sizes smaller than 32 Paris point), and 26 Paris point for children under three years of age.
Unless separately specified, the criteria apply to the final product which is composed of shoe uppers and outer soles that are made of homogeneous materials and articles that form the final product.
The applicant shall provide the bill of materials of the product, listing all homogeneous materials and articles used. The weight of each constituent material shall be expressed in grams and as a percentage of the shoe uppers and the shoe outer soles. The total final product unit weight shall be stated.
Criterion 6 refers to a Restricted Substances List which is provided in the Appendix. The list sets out the scope of restrictions and respective verification methods.
EU ECOLABEL CRITERIA
Criterion 1 — Origin of hides and skins, cotton, wood and cork, and man-made cellulose fibres, and plastics
1.1. Requirements on hides and skins
Raw hides and skins destined to be used in a final product shall be subject to the restrictions specified in criteria 1.1(a) and 1.1(b).
1.1(a)
Criterion 1.1(a) shall apply when the leather content in shoe uppers or shoe outer soles is greater than 10,0 % weight by weight of either component.
Only raw hides and skins from animals raised for milk or meat production are allowed to be used for the production of leather that is destined for use in the final product.
Assessment and verification: the applicant shall submit a declaration of compliance from the leather manufacturer or the hides or skins supplier. The declaration shall state that the leather manufacturing company conducts compliance verification checks on the raw materials used, and that the raw hides and skins destined to be used in the final product originate from animals raised for milk or meat production.
1.1(b)
Raw hides and skins originating from extinct, extinct in the wild, critically endangered, endangered, vulnerable, and near threatened species, according to the categories established by the International Union for Conservation of Nature (IUCN) Red List of Threatened Species ( 3 ), shall not be used in the final product.
Assessment and verification: the applicant shall provide a declaration of compliance from the leather manufacturer or leather supplier. The declaration shall identify the animal of origin and state that raw hides and skins destined to be used in a final product do not originate from extinct, extinct in the wild, critically endangered, endangered, vulnerable, or near threatened species according to the IUCN classification.
1.2. Cotton and other natural cellulosic seed fibres
Criterion 1.2 shall apply when the cotton content in shoe uppers or shoe outer soles is greater than 10,0 % weight by weight of either component.
Cotton that contains 70,0 % weight by weight or more of recycled content is exempted from the requirement of criterion 1.2.
Cotton and other natural cellulosic seed fibres (hereinafter referred to as cotton) that are not recycled fibres shall contain a minimum content of either organic cotton (see criterion 1.2(a) or integrated pest management (IPM) cotton (see criterion 1.2(b)).
Textiles that have been awarded the EU Ecolabel based on the ecological criteria of Commission Decision 2014/350/EU ( 4 ) are considered to comply with criterion 1.2.
Assessment and verification: the applicant or material supplier, as appropriate, shall provide a declaration of compliance.
Where EU Ecolabel textiles are used, the applicant shall provide a copy of the EU Ecolabel certificate showing that it was awarded in accordance with Decision 2014/350/EU.
Where applicable, recycled content shall be traceable back to the reprocessing of the feedstock. This shall be verified by independent third-party certification of the chain of custody or by documentation provided by feedstock suppliers and reprocessors.
1.2(a)
With the exception of footwear intended for children under three years of age, a minimum of 10 % weight by weight of the non-recycled cotton fibre used in the product shall be grown according to the requirements laid down in Council Regulation (EC) No 834/2007 ( 5 ), the US National Organic Programme (NOP) or equivalent legal obligations set by trading partners of the EU. The organic cotton content may include organically grown cotton and transitional organic cotton.
At least 95 % w/w of the non-recycled cotton fibre used in footwear intended for children under three years of age shall be organic cotton.
Where the organic cotton is to be blended with conventional or IPM cotton, cotton shall be from non-genetically modified varieties.
Organic content claims may only be made when the organic content is a minimum of 95 %.
Assessment and verification: the applicant or material supplier, as appropriate, shall provide a declaration of compliance for the organic content supported by evidence certified by an independent control body to have been produced in conformity with the production and inspection requirements laid down in Regulation (EC) No 834/2007, the US National Organic Programme (NOP) or those set by other trading partners. Verification shall be provided for each country of origin.
The applicant or material supplier, as appropriate, shall demonstrate compliance with the minimum organic cotton content requirement based on the annual volume of cotton purchased to manufacture the final product(s) and according to each product line. Transaction records and/or invoices shall be provided that document the quantity of certified cotton purchased.
For conventional or IPM cotton that is used in blends with organic cotton, a screening test for common genetic modifications shall be accepted as a proof of compliance of the cotton variety.
1.2(b)
With the exception of footwear intended for children under three years of age, a minimum of 20 % weight by weight of the non-recycled cotton fibre used in the product shall be grown according to IPM principles as defined by the UN Food and Agricultural Organisation (FAO) IPM programme or Integrated Crop Management (ICM) systems incorporating IPM principles.
At least 60 % of the non-recycled cotton fibre used in footwear intended for children under three years of age shall be grown according to IPM principles.
IPM cotton destined for use in the final product shall be grown without the use of any of the following substances: aldicarb, aldrin, camphechlor (toxaphene), captafol, chlordane, 2,4,5-T, chlordimeform, cypermethrin, DDT, dieldrin, dinoseb and its salts, endosulfan, endrin, heptachlor, hexachlorobenzene, hexachlorocyclohexane (total isomers), methamidophos, methylparathion, monocrotophos, neonicotinoids (clothianidine, imidacloprid, thiametoxam), parathion, pentachlorophenol.
Assessment and verification: the applicant or material supplier, as appropriate, shall provide a declaration of compliance with criterion 1.2(b), supported by evidence that at least 20 % weight by weight of the non-recycled cotton fibre contained in the product, or 60 % weight by weight in the case of footwear intended for children under three years of age, has been grown by farmers that have participated in formal training programmes of the UN FAO or Government IPM or ICM programmes and/or that have been audited as part of third-party-certified IPM schemes. Verification shall either be provided on an annual basis for each country of origin or on the basis of certifications for all IPM cotton purchased to manufacture the product.
The applicant or material supplier, as appropriate, shall also declare that the IPM cotton was not grown using any of the substances listed in criterion 1.2(b). IPM certification schemes that exclude the use of listed substances shall be accepted as proof of compliance.
1.3. Sustainable wood and cork
Criterion 1.3 shall apply when the wood or cork content used in shoe uppers or shoe outer soles is greater than 10,0 % weight by weight of either component.
All wood and cork shall be covered by chain of custody certificates issued by an independent third-party certification scheme such as the Forest Stewardship Council (FSC), the Programme for the Endorsement of Forest Certification (PEFC) or equivalent.
All virgin wood and cork shall not originate from GMO species and shall be covered by valid sustainable forest management and chain of custody certificates issued by an independent third-party certification scheme such as FSC, PEFC or equivalent.
Where a certification scheme allows the mixing of uncertified material with certified and/or recycled materials in a product or production line, a minimum of 70 % of the wood or cork material, as appropriate, shall be sustainable certified virgin material and/or recycled material.
Uncertified material shall be covered by a verification system which ensures that it is legally sourced and meets any other requirements of the certification scheme with respect to uncertified material.
The certification bodies issuing forest and/or chain of custody certificates shall be accredited or recognised by that certification scheme.
Assessment and verification: the applicant or material supplier, as appropriate, shall provide a declaration of compliance supported by valid, independently certified chain of custody certificate(s) for all wood and cork material used in the product or production line and demonstrate that at least 70 % of the wood or cork material originates from forests or areas managed according to sustainable forest management principles and/or from recycled sources that meet the requirements set out by the relevant independent chain of custody certification scheme. FSC, PEFC or equivalent schemes shall be accepted as independent third-party certification. In case the scheme does not specifically require that all virgin material is sourced from non-GMO species, additional evidence shall be provided to demonstrate this.
If the product or production line includes uncertified virgin material, proof shall be provided that the content of uncertified virgin material does not exceed 30 % and is covered by a verification system which ensures that it is legally sourced and meets any other requirements of the certification scheme with respect to uncertified material.
1.4. Man-made cellulose fibres (including viscose, modal and lyocell)
Criterion 1.4 shall apply when the man-made cellulose fibre content used in shoe uppers or shoe outer soles is greater than 10,0 % weight by weight of either component.
Man-made cellulose fibres that contain 70,0 % weight by weight or more of recycled content are exempted from the requirement of criterion 1.4.
A minimum of 25,0 % of the non-recycled pulp fibres shall be manufactured from wood that has been grown according to the principles of sustainable forest management as defined by the UN FAO. The remaining proportion of the non-recycled pulp fibres shall be from pulp that is sourced from legal forestry and plantations.
Textile products that have been awarded the EU Ecolabel based on the ecological criteria of Decision 2014/350/EU are considered to comply with criterion 1.4.
Assessment and verification: the applicant or material supplier, as appropriate, shall provide a declaration of compliance.
Where EU Ecolabel textile products are used, the applicant shall provide a copy of the EU Ecolabel certificate showing that it was awarded in accordance with Decision 2014/350/EU. Otherwise, the applicant shall obtain from the fibre manufacturer(s) valid, third-party certified chain of custody certificates demonstrating that the wood fibres have been grown according to sustainable forest management principles and/or are from legal sources. FSC, PEFC or equivalent schemes shall be accepted as independent certification.
The fibre manufacturer shall demonstrate that due diligence processes have been followed as specified in Regulation (EU) No 995/2010 of the European Parliament and of the Council ( 6 ) in order to ensure that timber has been legally harvested. Valid EU Forest Law Enforcement, Governance and Trade (FLEGT) or UN Convention on International Trade in Endangered Species of Wild Fauna and Flora (CITES) licences and/or third-party certification shall be accepted as evidence of legal sourcing.
Where applicable, recycled content shall be traceable back to the reprocessing of the feedstock. That shall be verified by independent third-party certification of the chain of custody or by documentation provided by feedstock suppliers and reprocessors.
1.5. Plastics
PVC plastic shall not be used in any part of the product.
Assessment and verification: the applicant or material supplier, as appropriate, shall provide a declaration of compliance.
Criterion 2 — Reduction of water consumption and restriction on the tanning of hides and skins
Raw hides and skins that are destined to be used in the final product shall be subject to the limit on water consumption in the tanning process as specified under criterion 2.1.
Leather used in products intended for children under three years of age shall be subject to the restriction on chromium-based tanning as specified under criterion 2.2.
2.1. Water consumption
The criterion shall apply when the leather content used in shoe uppers or shoe outer soles is greater than 10,0 % weight by weight of either component.
Water consumption expressed as the annual average volume of water consumed per tonne of raw hides and skins shall not exceed the limits given in Table 1.
Table 1
Maximum permitted water consumption in tanning processes
|
Hides |
28 m3/t |
|
Skins |
45 m3/t |
|
Vegetable tanned leather |
35 m3/t |
|
Pigskin |
80 m3/t |
|
Sheepskins |
180 l/skin |
Assessment and verification: the applicant shall provide a declaration of compliance from the leather supplier or leather manufacturing company, as appropriate. The declaration shall specify the annual amount of leather production and related water consumption based on the monthly average values of the last 12 months preceding the application, measured by the quantity of waste water discharged.
If the leather production process is conducted in different geographical locations, the applicant or supplier of semi-finished leather shall provide documentation that specifies the quantity of water discharged (m3) for the quantity of semi-finished leather processed in tonnes (t) or number of skins for sheepskin, as appropriate, based on the monthly average values during the 12 months preceding the application.
2.2. Restriction on the tanning of hides and skins
For footwear intended for children under three years of age, raw hides and skins destined to be used in linings and socks, as defined in Article 2(2), shall be processed using chromium-free tanning technology.
Assessment and verification: for footwear intended for children under three years of age, the applicant shall submit a declaration of compliance from the leather manufacturer or leather supplier, as appropriate, with the information that the leather used in the interior parts of the footwear (lining and/or socks) is chromium-free tanned. The declaration shall specify the tanning agent used in the processing of raw hides and skins.
Criterion 3 — Emissions to water from the production of leather, textiles and rubber
Textiles, leather and rubber that are destined to be used in the final product shall be subject to the limit on emissions to water.
The criterion shall apply whenever the leather, textile or rubber content, as appropriate, is used in shoe uppers or shoe outer soles and is greater than 10,0 % weight by weight of either component.
3.1. Chemical Oxygen Demand (COD) in waste water from leather tanning sites
The COD value in waste water from leather tanning sites, when discharged to surface waters after treatment (whether on site or off site), shall not exceed 200,0 mg/l.
Assessment and verification: the applicant or material supplier, as appropriate, shall provide a declaration of compliance supported by detailed documentation and test reports in accordance with ISO 6060 showing compliance with this criterion on the basis of monthly averages for the six months preceding the application. The data shall demonstrate the compliance of the production site or, if the effluent is treated off site, of the waste water treatment operator.
3.2. Chemical Oxygen Demand (COD) in waste water from textile finishing processes
The COD value in waste water discharges from textile finishing processes shall not exceed 20,0 g/kg of textiles processed.
Finishing processes shall include the thermosetting, thermosoling, coating and impregnating of textiles. This requirement shall apply to wet processes used in the finishing of the textile fabric. The requirement shall be measured downstream of an on-site waste water treatment plant or a municipal waste water treatment plant receiving waste water from these processing sites.
Textile products that have been awarded the EU Ecolabel based on the ecological criteria of Decision 2014/350/EU are considered compliant with criterion 3.2.
Assessment and verification: the applicant or material supplier, as appropriate, shall provide a declaration of compliance.
Where EU Ecolabel textile products are used, the applicant shall provide a copy of the EU Ecolabel certificate showing that it was awarded in accordance with Decision 2014/350/EU.
Otherwise, the applicant or material supplier, as appropriate, shall provide detailed documentation and test reports in accordance with ISO 6060, showing compliance with this criterion on the basis of monthly averages for the six months preceding the application. The data shall demonstrate the compliance by the production site or, if the effluent is treated off site, by the waste water treatment operator.
3.3. Chemical Oxygen Demand (COD) in waste water from the processing of natural and synthetic rubber
The COD value in waste water from the processing of natural or synthetic rubber, as applicable, when discharged to surface waters after treatment (whether on site or off site), shall not exceed 150,0 mg/l. This requirement shall apply to wet processes used to manufacture the rubber.
Assessment and verification: the applicant or material supplier, as appropriate, shall provide a declaration of compliance supported by detailed documentation and test reports, based on ISO 6060 showing compliance with this criterion on the basis of monthly averages for the six months preceding the application The data shall demonstrate compliance by the production site or, if the effluent is treated off site, by the waste water treatment operator.
3.4. Chromium in tannery waste water after treatment
The total chromium concentration in tannery waste water after treatment shall not exceed 1,0 mg/l as specified in Commission Implementing Decision 2013/84/EU ( 7 ).
Assessment and verification: the applicant or material supplier, as appropriate, shall provide a declaration of compliance supported by a test report using one of the following test methods: ISO 9174, EN 1233 or EN ISO 11885 for chromium and showing compliance with this criterion on the basis of monthly averages for the six months preceding the application. The applicant shall provide a declaration of compliance with BAT 10 and either BAT 11 or 12, as appropriate, of Implementing Decision 2013/84/EU for the reduction of the chromium content of waste water discharges.
Criterion 4 — Volatile organic compounds (VOCs)
Unless otherwise specified, the total use of VOCs in the final footwear production shall not exceed, on average, 18,0 g VOC/pair.
For footwear classified as personal protective equipment in accordance with Directive 89/686/EEC, the total use of VOCs during final footwear production shall not exceed, on average, 20,0 g VOC/pair.
Assessment and verification: the applicant shall provide a declaration of compliance supported by a calculation of the total use of VOCs during final shoe production in accordance with EN 14602. The calculation shall be supported by test results and documentation (registration of purchased leather, adhesives, finishes and production of footwear) as appropriate.
Where applicable, a copy of certification issued by a certification body notified under Directive 89/686/EEC that proves that the product is classified as personal protective equipment shall be provided.
Criterion 5 — Hazardous substances in the product and shoe components
The presence in the final product, and any homogeneous materials or articles thereof, of substances and mixtures that meet the criteria for classification according to Article 57 of Regulation (EC) No 1907/2006 of the European Parliament and of the Council ( 8 ) as substances of very high concern (SVHCs) or substances or mixtures that meet the criteria for classification, labelling and packaging (CLP) according to Regulation (EC) No 1272/2008 of the European Parliament and of the Council ( 9 ) for the hazards listed in Table 2 shall be restricted in accordance with criteria 5.1 and 5.2.
For the purposes of this criterion, the Candidate List of substances of very high concern (SVHCs) and CLP hazard classifications are grouped in Table 2 according to their hazardous properties.
The criterion does not apply to substances or mixtures which change their properties upon processing (in other words, substances which become no longer bioavailable or undergo chemical modification) such that the identified hazard no longer applies. This shall include chemical reactions where substances have been modified such as polymerisation where monomers or additives become covalently bonded.
Textile products that have been awarded the EU Ecolabel based on the ecological criteria of Decision 2014/350/EU are considered to comply with criterion 5.
Table 2
Grouping of restricted hazards
Group 1 hazards — Substances of very high concern (SVHC)
Hazards that identify a substance or mixture as being within Group 1:
Group 2 hazards — CLP hazards
Hazards that identify a substance or mixture as being within Group 2:
Group 3 hazards — CLP hazards
Hazards that identify a substance or mixture as being within Group 3:
5.1. Restriction of substances of very high concern
The final product, and any homogeneous materials or articles thereof, shall not contain substances that have been identified according to the procedure described in Article 59(1) of Regulation (EC) No 1907/2006 and included in the Candidate List for SVHCs in concentrations higher than 0,10 % weight by weight.
No derogation shall be given to Candidate List SVHCs if they are present in the final product, or to any homogeneous materials or articles that form part of the final product in concentrations higher than 0,10 % weight by weight.
The screening shall be based on the identification of the potential for presence of such substances in the product.
Assessment and verification: the applicant shall provide a declaration of compliance supported, where appropriate, by declarations from the material supplier regarding the absence of SVHCs at concentrations greater than 0,10 % (weight by weight) for the final product, and any homogeneous materials or articles that form part of the product. Declarations shall be referenced to the latest version of the Candidate List published by ECHA ( 11 ).
Where EU Ecolabel textile products are used, the applicant shall provide a copy of the EU Ecolabel certificate showing that it was awarded in accordance with Decision 2014/350/EU.
5.2. Restriction based on CLP classified substances and mixtures
With the exception of linings and socks, as defined in Article 2(2) of this Decision, the criterion shall apply when the content of any homogeneous material or article in shoe uppers or shoe outer soles is greater than 3,0 % (weight by weight) of either component. For linings and socks, any homogeneous material or article that is used for linings and socks shall be subject to the restriction as specified in the next paragraph.
Substances and mixtures falling within the groups identified in Table 3 that meet the criteria for classification with the CLP hazards in Table 2 shall not be present in any homogeneous materials or articles that form part of the final product in concentrations higher than 0,10 % (weight by weight).
Table 3
Substances and mixtures groups to which criterion 5.2 shall apply
The use of certain substances and mixtures referred to in Table 3 is exempted from the requirements of criterion 5.2 subject to the conditions specified in Table 4.
Table 4
Derogation conditions that shall apply to the use of functional substances and mixtures
|
Substances and mixtures |
Scope of derogation |
Derogation conditions |
Applicability to footwear |
|
Nickel |
H317, H351, H372 |
Nickel can only be contained in stainless steel. A nickel release rate from the stainless steel shall be less than or equal to 0,5 μg/cm2/week as specified in criterion 6 (RSL). |
Metal toecaps and footwear accessories |
|
Dyestuffs for dyeing and non-pigment printing |
H301, H311, H331, H317 |
Dust-free dye formulations or automatic dosing and dispensing of dyes shall be used by dye houses and printers to minimise worker exposure. |
Dyestuffs |
|
Dyestuffs for dyeing and non-pigment printing |
H411, H412, H413 |
Dyeing processes using reactive, direct, vat, or sulphur dyes with these classifications shall meet a minimum of one of the following conditions: 1. Use of high affinity dyes; 2. Achievement of a reject rate of less than 3,0 %; 3. Use of colour matching instrumentation; 4. Implementation of standard operating procedures for the dyeing process; 5. Use of colour removal to treat waste water. The use of solution dyeing and/or digital printing is exempted from these conditions. |
Dyestuffs |
|
Water, dirt and stain repellents |
H413 |
The repellent and its degradation products shall be readily and/or inherently biodegradable and non-bioaccumulative substances in the aquatic environment, including aquatic sediment. |
Water repellence |
|
Residual auxiliaries found in any homogeneous materials or articles that form part of the final product |
|||
|
Auxiliaries comprising: carriers, levelling agents, dispersing agents, surfactants, thickeners, binders |
H301, H311, H331, H371, H373, H317 (1B), H411, H412, H413, EUH070, |
Recipes shall be formulated using automatic dosing systems and processes shall follow standard operating procedures. Substances classified with H311, H331, H317 (1B) shall not be present at concentrations greater than 1,0 % w/w in any homogeneous material or article that forms part of the final product. |
Auxiliaries |
Assessment and verification: the applicant shall provide a declaration of compliance with criterion 5.2 supported, where appropriate, by declarations from the material supplier(s). The declaration shall be supported by a list of the substances and/or substances in mixtures as specified in Table 3 that are present in any homogeneous material or article that forms part of the final product, together with information about their hazard classification or non-classification.
The following information shall be provided to support declarations of the hazard classification or non-classification for each substance or mixture:
When considering self-classification entries in the REACH registered substance database, priority shall be given to entries from joint submissions.
Where a classification is recorded as ‘data lacking’ or ‘inconclusive’ according to the REACH registered substance database, or where a substance has not yet been registered under the REACH regulation, toxicological data meeting the requirements in Annex VII to Regulation (EC) No 1907/2006 shall be provided that are sufficient to support conclusive self-classification in accordance with Annex I to Regulation (EC) No 1272/2008 and ECHA's supporting guidance. In the case of ‘data lacking’ or ‘inconclusive’ database entries, self-classifications shall be verified, with the following information sources being accepted:
Information on the hazardous properties of substances or mixtures may, in accordance with Annex XI to Regulation (EC) No 1907/2006, be generated by means other than tests, for instance through the use of alternative methods such as in vitro methods, by quantitative structure activity models or by the use of grouping or read-across.
For the derogated substances and mixtures listed in Table 4, the applicant shall provide proof that all the derogation conditions are met.
Where EU Ecolabel textile products are used, the applicant shall provide a copy of the EU Ecolabel certificate showing that it was awarded in accordance with Decision 2014/350/EU.
Criterion 6 — Restricted Substances List (RSL)
The criterion shall apply when any homogeneous material or article used in shoe uppers or shoe outer soles is greater than 3,0 % weight by weight of either component.
The final product, homogeneous materials or articles that form part of the final product, or production recipes used, as applicable, shall not contain substances specified under the Restricted Substances List (RSL). The applicability, scope of restrictions, verification and testing requirements are provided in the RSL for each substance or group of substances. The RSL can be found in the Appendix to this Decision.
The RSL shall be communicated by the applicant to all the suppliers of materials or articles that will be used as components of the EU Ecolabel product.
Textile products that have been awarded the EU Ecolabel based on the ecological criteria of Decision 2014/350/EU are considered to comply with criterion 6.
Assessment and verification: the applicant and their material supplier(s), as appropriate, shall provide a declaration of compliance with the RSL supported by evidence that is applicable to the substances and mixtures used to manufacture the final product or its materials. Verification shall be provided for each relevant requirement as indicated in the RSL, which may include:
Where required, Safety Data Sheets shall be completed in accordance with the guidance in Sections 10, 11 and 12 of Annex II to Regulation (EC) No 1907/2006 (Requirements for the Compilation of Safety Data Sheets). Incomplete Safety Data Sheets (SDS) will require supplemental declarations from chemical suppliers.
Where laboratory analysis of the final product is required, it shall be performed for specific product lines and based on random sampling. Where specified, it shall be carried out annually during the licence period in order to demonstrate ongoing compliance with the RSL criterion with results then communicated to the relevant competent body.
Test data obtained for the purposes of compliance with industry RSLs and other footwear certification schemes shall be accepted where the test methods are equivalent.
Where EU Ecolabel textile products are used, the applicant shall provide a copy of the EU Ecolabel certificate showing that it was awarded in accordance with Decision 2014/350/EU.
Criterion 7 — Parameters contributing to durability
Occupational and safety footwear shall carry the CE mark and shall meet the durability requirements specified in accordance with Directive 89/686/EEC. All other footwear shall meet the requirements indicated in Table 5.
Table 5
Durability parameters
|
Parameter/Standard test method |
General sports |
School footwear |
Casual |
Men's town |
Cold weather footwear |
Women's town |
Fashion |
Infants |
Indoor |
|
|
Uppers' flex resistant: (kc without visible damage)/EN 13512 |
Dry = 100 Wet = 20 |
Dry = 100 Wet = 20 |
Dry = 80 Wet = 20 |
Dry = 80 Wet = 20 |
Dry = 100 Wet = 20 – 20° = 30 |
Dry = 50 Wet = 10 |
Dry = 15 |
Dry = 15 |
Dry = 15 |
|
|
Uppers' tear strength (Average tear force, N)/EN 13571 |
Leather |
≥ 80 |
≥ 60 |
≥ 60 |
≥ 60 |
≥ 60 |
≥ 40 |
≥ 30 |
≥ 30 |
≥ 30 |
|
Other materials |
≥ 40 |
≥ 40 |
≥ 40 |
≥ 40 |
≥ 40 |
≥ 40 |
≥ 30 |
≥ 30 |
≥ 30 |
|
|
Outsoles' flex resistance: EN 17707 |
Cut growth (mm) Nsc = no spontaneous crack |
≤ 4 Nsc |
≤ 4 Nsc |
≤ 4 Nsc |
≤ 4 Nsc |
≤ 4 Nsc at – 10 °C |
≤ 4 Nsc |
|
|
|
|
Outsoles' abrasion resistance/EN 12770 |
D ≥ 0,9 g/cm3 (mm3) |
≤ 200 |
≤ 200 |
≤ 250 |
≤ 350 |
≤ 200 |
≤ 400 |
|
|
≤ 450 |
|
D < 0,9 g/cm3 (mg) |
≤ 150 |
≤ 150 |
≤ 170 |
≤ 200 |
≤ 150 |
≤ 250 |
|
|
≤ 300 |
|
|
Upper-sole adhesion (N/mm)/EN 17708 |
≥ 4,0 |
≥ 4,0 |
≥ 3,0 |
≥ 3,5 |
≥ 3,5 |
≥ 3,0 |
≥ 2,5 |
≥ 3,0 |
≥ 2,5 |
|
|
Outsoles' tear strength (Average strength, N/mm)/EN 12771 |
D ≥ 0,9 g/cm3 |
8 |
8 |
8 |
6 |
8 |
6 |
5 |
6 |
5 |
|
D < 0,9 g/cm3 |
6 |
6 |
6 |
4 |
6 |
4 |
4 |
5 |
4 |
|
|
Colour fastness of the inside of the footwear (lining or inner face of the upper). Grey scale on the felt after 50 cycles wet/EN ISO 17700 |
≥ 2/3 |
≥ 2/3 |
≥ 2/3 |
≥ 2/3 |
≥ 2/3 |
≥ 2/3 |
|
≥ 2/3 |
≥ 2/3 |
|
|
Linings' and socks' abrasion cycles/EN 17704 |
> 25 600 dry > 12 800 wet |
> 25 600 dry > 12 800 wet |
> 25 600 dry > 12 800 wet |
> 25 600 dry > 6 400 wet |
> 25 600 dry > 12 800 wet |
> 25 600 dry > 6 400 wet |
> 25 600 dry > 3 200 wet |
>= 25 600 dry >= 12 800 wet |
> 8 400 dry > 1 600 wet |
|
Assessment and verification: the applicant shall provide a declaration of compliance supported by test reports as specified in Table 5.
Where applicable, a copy of the certification issued by a certification body notified under Directive 89/686/EEC that proves that the product is classified as personal protective equipment shall be provided.
Criterion 8 — Corporate Social Responsibility with regard to labour aspects
Requirements in this criterion shall apply to the final footwear assembly site.
Having regard to the International Labour Organisation's (ILO) Tripartite Declaration of Principles concerning Multinational Enterprises and Social Policy, the UN Global Compact (Pillar 2), the UN Guiding Principles on Business and Human Rights and the OECD Guidelines for Multinational Enterprises, the applicant shall obtain third-party verification supported by site audit(s) that the applicable principles included in the ILO's fundamental conventions and the supplementary provisions below have been respected at the final footwear assembly site for the product.
Fundamental conventions of the ILO:
Child Labour:
Forced and Compulsory Labour:
Freedom of Association and Right to Collective Bargaining:
Discrimination:
Supplementary provisions:
Working Hours:
Remuneration:
Health & Safety:
In locations where the right to freedom of association and collective bargaining are restricted under law, the company shall recognise legitimate employee associations with whom it can enter into dialogue about workplace issues.
The audit process shall include consultation with external stakeholders in local areas around sites, including trade unions, community organisations, NGOs and labour experts. The applicant shall publish the aggregated results and key findings from the audit online in order to provide evidence of their supplier's performance to interested consumers.
Assessment and verification: the applicant shall provide a declaration of compliance together with copies of certificates and a supporting audit reports for each final product assembly plant for the model(s) to be ecolabelled.
The third-party site audit shall be carried out by private auditors qualified to assess the compliance of the footwear industry supply chain with social standards or codes of conduct or, in countries where the ILO Labour Inspection Convention, 1947 (No 81) has been ratified and ILO supervision indicates that the national labour inspection system is effective ( 15 ) and where the scope of the inspection systems covers the areas listed above, by labour inspector(s) appointed by a national authority.
Certificate(s), not dated more than 12 months prior to the application, from schemes or processes that audit compliance with the applicable principles of the listed fundamental ILO conventions, together with the supplementary provisions on working hours, remuneration and health and safety, shall be accepted.
Criterion 9 — Packaging
This criterion applies only to primary packaging, as defined in European Parliament and Council Directive 94/62/EC ( 16 ).
9.1. Cardboard and paper
Cardboard and paper used for the final packaging of footwear shall be made of 100 % recycled material.
9.2. Plastic
Plastic used for the final packaging of footwear shall be made of at least 80 % recycled material.
Assessment and verification: the applicant or packaging supplier, as appropriate, shall provide a declaration of compliance specifying the material composition of the packaging and the shares of recycled and virgin material.
Criterion 10 — Information on the packaging
10.1. User Instructions
The following information shall be supplied with the product:
Assessment and verification: the applicant shall provide a packaging sample or the proposed artwork of the packaging showing the user instructions that will be supplied with the product.
10.2. Information appearing on the EU Ecolabel
If the optional label with a text box is used, it shall contain, where relevant, three of the following statements:
natural origin raw materials sustainably managed (in case criterion 1 applies);
reduced pollution in production processes;
minimised use of hazardous substances;
tested for durability;
xx % organic cotton used (this claim may be made only if, based on criterion 1.2(a), more than 95 % of the total cotton is organic).
The guidelines for the use of the optional label with a text box can be found in the ‘Guidelines for use of the Ecolabel logo’ on the website:
http://ec.europa.eu/environment/ecolabel/documents/logo_guidelines.pdf
Assessment and verification: the applicant shall provide a declaration of compliance together with a sample of the product label or the proposed artwork showing where the EU Ecolabel is placed.
( 3 ) http://www.iucnredlist.org/
( 4 ) Commission Decision 2014/350/EU of 5 June 2014 establishing the ecological criteria for the award of the EU Ecolabel for textile products (OJ L 174, 13.6.2014, p. 45).
( 5 ) Council Regulation (EC) No 834/2007 of 28 June 2007 on organic production and labelling of organic products and repealing Regulation (EEC) No 2092/91 (OJ L 189, 20.7.2007, p. 1).
( 6 ) Regulation (EU) No 995/2010 of the European Parliament and of the Council of 20 October 2010 laying down the obligations of operators who place timber and timber products on the market (OJ L 295, 12.11.2010, p. 23).
( 7 ) Commission Implementing Decision 2013/84/EU of 11 February 2013 establishing the best available techniques (BAT) conclusions under Directive 2010/75/EU of the European Parliament and of the Council on industrial emissions for the tanning of hides and skins (OJ L 45, 16.2.2013, p. 13).
( 8 ) Regulation (EC) No 1907/2006 of the European Parliament and of the Council of 18 December 2006 concerning the Registration, Evaluation, Authorisation and Restriction of Chemicals (REACH), establishing a European Chemicals Agency (OJ L 136, 29.5.2007, p. 3).
( 9 ) Regulation (EC) No 1272/2008 of the European Parliament and of the Council of 16 December 2008 on classification, labelling and packaging of substances and mixtures, amending and repealing Directives 67/548/EEC and 1999/45/EC, and amending Regulation (EC) No 1907/2006 (OJ L 353, 31.12.2008, p. 1).
( 10 ) European Chemical Agency (ECHA), Candidate List of substances of very high concern for Authorisation, http://www.echa.europa.eu/candidate-list-table.
( *1 ) STOT = Specific target organ toxicity.
( 11 ) ECHA, Candidate List of substances of very high concern for Authorisation, http://www.echa.europa.eu/candidate-list-table
( 12 ) ECHA, REACH registered substances database, http://www.echa.europa.eu/information-on-chemicals/registered-substances
( 13 ) ECHA, Cooperation with peer regulatory agencies, http://echa.europa.eu/en/about-us/partners-and-networks/international-cooperation/cooperation-with-peer-regulatory-agencies
( 14 ) Social Accountability International, Social Accountability 8000 International Standard, http://www.sa-intl.org
( 15 ) See ILO NORMLEX (http://www.ilo.org/dyn/normlex/en) and supporting guidance.
( 16 ) European Parliament and Council Directive 94/62/EC of 20 December 1994 on packaging and packaging waste (OJ L 365, 31.12.1994, p. 10).