Footwear Ecolabel Criteria revision - European...

19
ria revision g Footwear Ecolabel Criter I EUEB meeting EUEB Meeting Brussels, 3 December 2008 Service Contract N. 070307/2007/482665/MAR/G2

Transcript of Footwear Ecolabel Criteria revision - European...

Page 1: Footwear Ecolabel Criteria revision - European Commissionec.europa.eu/environment/archives/ecolabel/pdf/... · Footwear Ecolabel Criteria revision I EUEB meeting New Criteria Proposal

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EUEB Meeting

Brussels, 3 December 2008

Service Contract N. 070307/2007/482665/MAR/G2

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gSTRUCTURE OF THE PLAN

Work Package 1Work Package 1

Development of a Preliminary Report for the evaluation of the necessity of revision for the existing criteria for Footwear product group

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Work Package 2Work Package 2

Revision of the existing criteria

for the allocation of the EU Eco-label to Footwear products.

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TASK ACTION DEADLINE Deliverables Status

TASK 1

Beginning of the project 17 December 2007 WP1 timetable Ok

1° AHWG meeting 12 March 2008

Preliminary Draft

Report;

PPT presentation

Ok

Minutes of the 1st AHWG meeting 26 March 2008 Minutes Ok

Management of the AHWG comments 26 March 2008Updated Preliminary

Draft Report Ok

Preliminary draft Report on the WP1 activities

diffusion to EC27 October 2008

Preliminary Draft Report

Ok

Comments from EC -Ok

WP1 activities: up to date situation (Table 1.1 in the Report)

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g Comments from EC -

Task 2

Management of EC and stakeholders comments on

Preliminary draft report and distribution to all interested

parties

27 October 2008

-

Ok

Final WP1 report preparation (containing an LCA study

for footwear production)

Final Draft Report

1st Background Report

Ok

First Background report (integrated in the WP1 Report)

First Draft criteria proposal 1° draft criteria Ok

Documents for the 1° AHWG MeetingFinal Draft Report

1° draft criteriaOk

II AHWG meeting 10 November 2008

Preliminary Draft

Report;

PPT presentation

Ok

Minutes of the 2nd AHWG meeting In 2 weeks Minutes Ok

Management of the AHWG comments In 2 weeks Draft Report Ok

Task 3Documentation for the EUEB meeting 19 November

2nd Draft criteria

ppt presentationOk

EUEB meeting 3 December - Ok

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gNew Criteria Proposal Framework

1. RESIDUES IN THE FINAL PRODUCT

2. REDUCTION OF WATER CONSUMPTION (FOR THE TANNING

OF HIDES AND SKINS)

3. EMISSIONS FROM THE PRODUCTION OF MATERIAL

4. USE OF HARMFUL SUBSTANCES

5. USE OF VOCS DURING FINAL ASSEMBLY OF SHOES

Modified

New criterion proposal

Modified

Updated and extended

Modified

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g 5. USE OF VOCS DURING FINAL ASSEMBLY OF SHOES

6. USE OF PVC

7. ENERGY CONSUMPTION

7. ELECTRIC COMPONENTS

8. PACKAGING OF THE FINAL PRODUCT

9. INFORMATION ON THE PACKAGING

10. INFORMATION APPEARING ON THE ECO-LABEL

11. PARAMETERS CONTRIBUTING TO DURABILITY

Modified

To be discussed

Made mandatory

DELETED - included in the PG definition (art. 2)

Modified

To be discussed at the end of the revision

To be discussed at the end of the revision

Modified

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gARTICLE 2

DEFINITION OF THE PRODUCT GROUP

Modification proposal

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The product group ‘footwear’ shall comprise:

“All articles of clothing designed to protect or cover the foot, with a fixed outer sole which comes

into contact with the ground.

Footwear shall not contain any electric or electronic components.”

The exclusion of the electric and electronic

components, currently required in the criterion

7, has been moved in the definition of the PG.

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gCRITERIA PREMISE

APPLICATION OF THE CRITERIA

New proposal

SOLUTION A SOLUTION B

The topside shoe components weighting less

SOLUTION C

The topside shoe components weighting less

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Former criteria:

no requirements

The topside shoe components weighting less

than 5% of the whole topside part shall not be

taken into account for the application of the

following criteria.

The bottom side shoe components weighting

less than 5% of the whole outer sole shall not

be taken into account for the application of

the following criteria.

The topside shoe components weighting less

than 3% of the whole topside part shall not be

taken into account for the application of the

following criteria.

The bottom side shoe components weighting

less than 3% of the whole outer sole shall not

be taken into account for the application of

the following criteria.

To facilitate the award, avoiding expensive and

useless tests on negligible parts of the shoe

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gCRITERION 1

RESIDUES IN THE FINAL PRODUCT

(a) Chromium (for leather only)

The average concentration of residuesof Chromium (VI) in the final productfor shoes made of leather shall notexceed 3 ppm or shall not be

detectable.

(b) Arsenic, Cadmium and Lead

The residues of Arsenic, Cadmium andLead shall not be detected in thematerials used for the productassembly or in the final product (usingthe method specified below).

(c) Formaldehyde

The amount of free and hydrolysatedformaldehyde of the components of thefootwear shall not exceed the followinglimits:

SOLUTION 2.A

Textile:

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SOLUTION A

Former criteria: no exceptions.

or

SOLUTION B

This requirement shall not apply if the tanning process is chrome free.

Assessment and verification: test methods EN ISO 17075

Assessment and verification: test methods EN 14602.

The applicant can choose whether apply the tests to the

“materials for the product assembly” or to the “final product”

Textile:

Children shoes (0-12) = 20 ppm (n.d.);

Other shoes = 75 ppm.

Leather shoes = 150 ppm.

Or

SOLUTION 2.B

Textile: 20 ppm (non detectable);

Leather = 150 ppm.

Assessment and verification

Textiles: EN ISO 14184-1;

Leather: EN 14602 or EN ISO 17226-1 or 2�Restriction only to leather shoes

because Cr (VI) derives from the leather

treatments only;

�Lowering of the limit for Cr(VI) to EN

ISO 17075 limit of detection .

Possibility to apply the criterion either to

the final product or to the materials

used for the assembly to limit the costs

of the grinding method application.

�Textile limit in agreement with the EU Ecolabel for Textiles and the OEKO TEX 100.

�Introduction of a new limit for children products lowering to a unique limit;

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gCRITERION 2

REDUCTION OF WATER CONSUMPTION (only for the tanning of hides and skins)

New proposal

The following limits to water consumption for the tanning of hide and skin shall not be exceeded:

Hides: 35 m3/t;

Skins: 55 m3/t

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g Skins: 55 m /t

Assessment and verification: the applicant and/or his supplier(s) shall provide a declaration that the mentioned limits have not been exceeded.

�The proposal has been developed in collaboration with COTANCE (European Leather Industry);

�Many literature references demonstrate both the strictness and the achievability of this limits.

�Some stakeholders ask to delete this new proposal because of the difficulties in calculating a realistic

and verifiable value for the water consumption related to the final product considered the many

successive stages composing the production process.

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EMISSIONS FROM THE PRODUCTION OF MATERIAL

(a) COD

The content of COD in waste waters from the textile and tanning

industries discharged into superficial waters after treatment in in-

house and/or municipal waste water treatment plants/facilities, shall

(b) Chromium III

Tannery waste water after treatment shall

contain less than 5 mg Chromium (III)/l.

CRITERION 3 (ex criterion 2)

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g house and/or municipal waste water treatment plants/facilities, shall

not exceed 150mg COD/l of water discharged.

Assessment and verification: the applicant shall provide a test report

and complementary data, using the following test method: COD: ISO

6060 - Water quality, determination of chemical oxygen demand.

Assessment and verification: the applicant

shall provide a test report and

complementary data, using the following

test methods: ISO 9174 or EN 1233 or EN

ISO 11885 for Cr.

� The proposal has been developed in collaboration with COTANCE

(European Leather Industry);

� The more restrictive law hurdles in Europe are of 150-160 mg/l (125

mg/l of COD in the effluent water for treatment plants to urban waste

water);

� The previous requirement (85% reduction, was unsuitable).

No modification

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gCRITERION 4 (ex criterion 3)

USE OF HARMFUL SUBSTANCES (UP UNTIL PURCHASE)

(a) PCP and TCP

a) Pentachlorophenol (PCP) andTetrachlorophenol (TCP) and theirsalts and esters shall not be used.

Textiles: limit value 0,05 ppm

(b) Azo dyes

b) No azo dyes shall be used that maycleave to any of the following aromaticamines:

[for the list of substances, please, refer

(c) N-Nitrosamines

(d) Chloralkanes

(c) The following N-Nitrosamines shall notbe detected in rubber.

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Textiles: limit value 0,05 ppm

Leather: limit value 5 ppm

Assessment and verification: [...] Should a verification of this

declaration be carried out, the following test methods shall be used: Leather (EN ISO 17070): limit value 5

ppm; Textile (XP G 08-015): limit value 0,05 ppm;

[for the list of substances, please, referto the Commission Decision2002/231/EC.]

Textiles: EN 14362 1 or 2 - limit 30 ppm

Leather: CEN ISO TS 17234 - limit 30ppm.

be detected in rubber.

[for the list of substances, please, refer tothe Commission Decision 2002/231/EC]

Assessment and verification: test methodsEN 12868 (1999-12) or EN 14602.

(d) C10-C13 chloralkanes shall not be usedin leather, rubber or textile components.

Assessment and verification: declarationof non use.

It is impossible to ask a reduction since

the limit cannot be detected, also I they

matches with the Directive 2002/61/EC

Updated

Updated

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gCRITERION 4 (ex criterion 3)

USE OF HARMFUL SUBSTANCES (UP UNTIL PURCHASE)

(e) Carcinogenic, mutagenic or toxic to reproduction dyes

(e) The following dyes classified as carcinogenic, mutagenic or toxic to

reproduction shall not be used to dye

(f) NPE and PFOS

(f) Nonylphenol ethoxylate (NPE) andPerfluorooctane sulfonate (PFOS) shallnot be used.

(g) Disperse dyes

(g) The following substances classified as“potentially sensitising dyes” shall not beused:

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g reproduction shall not be used to dye the materials used for the final

product assembly:

[for the list of substances, please, refer to the Commission Decision

2002/231/EC.]

Assessment and verification: [...] declaration of non-use

not be used.

Assessment and verification: theapplicant shall provide a declaration ofnon-use.

used:

[for the list of substances, please, refer tothe Commission Decision 2002/231/EC.]

Assessment and verification: [...]declaration of non-use

NEW CRITERION

Harmonised with

the EU Ecolabel for

Textile products

NEW CRITERION

NEW CRITERION

Harmonised with

the EU Ecolabel for

Textile products

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USE OF VOLATILE ORGANIC COMPOUNDS (VOCS) DURING FINAL ASSEMBLY OF SHOES

Modification proposal

SOLUTION A SOLUTION B SOLUTION C

CRITERION 5 (ex criterion 4)

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To delete the criterion because as it

is now (25 grams VOC/pair) it

matches with the current in force

legislation

The total use of VOCs during final

footwear production, for the following

categories, shall not exceed, on

average, 20 grams VOC/pair.

The total use of VOCs during final

footwear production, for the following

categories, shall not exceed, on

average, 15 grams VOC/pair.

Directive 1999/13/CE allows a

maximum limit of limit of 25 gram

VOC/pair

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gCRITERION 6 (ex criterion 5)

USE OF PVC

Modification proposal

SOLUTION A (old criterion)

The footwear shall not contain virgin

PVC.

Recycled PVC may, however, be used in

outsoles, where no use is made of

SOLUTION B

If PVC is used it must comply with the Directive 2005/84/CE on phthalates, which

provide the limitation and exclusion of some components. In particular, it is

forbidden to the use of the following substances, which are also prioritised under

the EChA SVHC (Substances of Very High Concern) list:

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outsoles, where no use is made of

DEHP (bis(2-ethylhexyl)phthalate), BBP

(butylbenzylphthalate) or DBP

dibutylphthalate) in preparing the

polymer.

Assessment and verification:

declaration of compliance.

Bis (2-ethyl(hexyl)phthalate) (DEHP)

Benzyl butyl phthalate (BBP)

dibutylphthalate (DBP)

The “PVC MADE” label is requested on the shoes (or pack). An information

concerning the content (in %) of virgin/recycled PVC contained in the shoes must be

put on the product packaging.”

Finally, the applicant is requested to provide evidences of the wiliness to make

feasible a suitable and practicable way to collect shoes at the end of their life for

recycling.

Assessment and verification: declaration of compliance and participation with

recycling schemes like Vinyl 2010 or other PVC recycling schemes.

No modification

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ENERGY CONSUMPTION

Modification proposal (IT BECOMES MANDATORY)

The energy consumption at the manufacturing stage shall be declared.

Assessment and verification: the applicant is requested to provide the relevant information according to the

Technical appendix A1.

CRITERION 7 (ex criterion 6)

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Technical Appendix A1. Energy consumption calculation

The average electric consumption (AEC) for each pair of shoes can be calculated two alternative ways:

On the base of the standard daily production of the

plant:

- MJdp = direct energy used in daily production

[electricity + fossil fuels] as annual average;

- N = number of shoes daily produced as annual

average.

On the base of the effective ecolabelled production

of the plant:

- MJep = MJ used in the production of the

Ecolabelled shoes [electricity + fossil fuels] as

annual (annual data);

- Nep = number of Ecolabelled shoes produced as

annual data.

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gCRITERION 8

PACKAGING OF THE FINAL PRODUCT

Modification proposal

Where cardboard boxes are used for the final Where plastic bags are used for the final

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packaging of footwear, they shall be made from

a minimum of 100 % recycled material.

packaging of footwear, they shall be made from

at least 50% recycled material.

•The proposal to introduce a requirement for

the biodegradability of sacks and bag was

made;

• The relevance of this requirement has to be

investigated.

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The criteria report some basic recommendations about the product correct use, as:

‘These shoes have been treated to improve their water resistance. They do not require further

treatment.’

‘Where possible repair your footwear rather than throw them away. This is less damaging to the

environment.’

CRITERION 9. – INFORMATION OF THE PACKAGING

The proposed modifications have to be

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‘When disposing of footwear, please use appropriate local recycling facilities where these are

available.’

The decision text cites:

“Box 2 of the eco-label shall contain the following text:

- low air and water pollution,

- harmful substances avoided.”

CRITERION 10. –INFORMATION APPEARING ON THE ECO-LABEL

The proposed modifications have to be

discussed at the end of the revision

process, according to the other criteria

changes and to the Ecolabel Regulation.

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General sports School footwear Casual Men’s townCold weather

footwearWomen’s town Fashion Infants Indoor

Uppers flex resistant:

(kc without visible damage)

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)

Leather

Other materials

≥ 80

≥ 40

≥ 60

≥ 40

≥ 60

≥ 40

≥ 60

≥ 40

≥ 60

≥ 40

≥ 40

≥ 40

≥ 30

≥ 30

≥ 30

≥ 30

≥ 30

≥ 30

Outsoles flex resistance:

CRITERION 11 - PARAMETERS CONTRIBUTING TO DURABILITY

The value for the categories “school” and “casual” has been interchanged

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g Outsoles flex resistance:

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:

D ≥ 0,9 g/cm3 (mm3)

D < 0,9 g/cm3 (mg)

≤ 200

≤ 150

≤ 200

≤ 150

≤ 250

≤ 170

≤ 350

≤ 200

≤ 200

≤ 150

≤ 400

≤ 250

≤ 450

≤ 300

Uppersole adhesion: (N/mm) ≥ 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)

D ≥ 0,9 g/cm3

D < 0,9 g/cm3

8

6

8

6

8

6

6

4

8

6

6

4

5

4

6

5

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

≥ 2/3 ≥ 2/3 ≥ 2/3 ≥ 2/3 ≥ 2/3 ≥ 2/3 ≥ 2/3 ≥ 2/3

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gFOOTWEAR ECOLABELLING AND DEVELOPING COUNTRIES

LCE has been invited to participate to two project promoted by UNEP for the

“ENABLING DEVELOPING COUNTRIES TO SEIZE ECO-LABELLING

OPPORTUNITIES”.

1er Taller Nacional de Ecoetiquetado – México Promoviendo oportunidades de ecoetiquetado

en países en desarrollo

(Attended by CIMAC).

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Regional workshop on eco-labelling, 17-18th september, 2008, at

the Silver Springs Hotel, Nairobi – Kenya;

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Life Cycle Engineering

Gian Luca Baldo

Marco Montani

60, Via Livorno- edificio A2

10144 Torino- Italy

Ph. +39 0112257311

Fax +39 0112257319

Email: montani@studiolce .it

Website : www.studiolce.it

For specific technical questions please write

to:

[email protected]