Grundnotat om EU-miljømærke til håndopvaskemidler
Modtaget via elektronisk post. Der tages forbehold for evt. fejl
Europaudvalget
(Alm. del - bilag 1042)
miljøministerråd
(Offentligt)
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Europaudvalg og deres stedfortrædere |
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Bilag |
Journalnummer |
Kontor |
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Til underretning for Folketingets Europaudvalg vedlægges Miljø- og Energiministeriets notat samt grundnotat om forslag til Kommissionens beslutning om miljøkriterier for tildeling af EU-miljømærke til håndopvaskemidler.
MILJØ
styrelsen Den 30. marts 2001Internationalt kontor J.nr M 1034-0051
OK/6
NOTAT TIL FOLKETINGETS EUROPAUDVALG
Om forslag til Kommissionens beslutning om miljøkriterier for tildeling af EU-miljømærke til håndopvaskemidler.
Kommissionen har fremlagt et forslag om miljøkriterier for tildeling af EU-miljømærke til håndopvaskemidler.
Formålet med den frivillige positive miljømærkeordning er at fremme udformningen, fremstillingen, markedsføringen og anvendelsen af produkter, som har mindsket indvirkning på miljøet gennem hele deres livscyklus samt give forbrugerne bedre information om produktets indvirkning på miljøet.
Det sker gennem fastlæggelse af en række kriterier, som skal overholdes for at kunne anvende miljømærket.
Beslutningsforslaget indeholder kriterier for tildeling af miljømærket Blomsten til håndopvaskemidler. Kommissionen har, med Frankrig som ledende kompetent organ, udarbejdet forslaget.
Forslaget har været til høring i EF-specialudvalget for miljø.
Der stemmes om forslaget den 6.april 2001.
Danmark agter at stemme for forslaget, idet der dog lægges afgørende vægt på kriterieforslagets
Krav om anaerob nedbrydelighed bibeholdes, som der er foreslået i udkastet.
MILJØ
styrelsen 30. marts 2001Kontoret for Renere Produkter J. nr. M 1034-0051
Grundnotat
om forslag til Kommissionens beslutning om miljøkriterier for tildeling af EU-miljømærket til håndopvaskemidler
1. Indledning
Kommissionen har den 28. februar 2001 fremsendt endeligt forslag til Kommissionens beslutning om etablering af miljøkriterier for tildeling af EU-miljømærket til håndopvaskemidler (Dok. ENV/2001/0043, draft 21 February 2001, engelsk udgave foreligger og er vedlagt).
Forslaget udgør en opfølgning af artikel 4 og 6 i Europa-Parlamentets og Rådets forordning nr. 1980/2000 af 17. juli 2000 om en revideret ordning for tildeling af EF-miljømærke. I disse artikler bestemmes det, at der fastsættes specifikke miljømærkekriterier for hver produktgruppe for en given gyldighedsperiode. Kriterier og gyldighedsperiode fastlægges i overensstemmelse med fremgangsmåden i art. 17, som er en forskriftsudvalgsprocedure, ef ter høring af Det Europæiske Miljømærkenævn.
Det er planlagt at Forskriftsudvalget skal stemme om sagen d. 6. april 2001. Det er dog endnu uklart om der vil blive truffet en endelig afgørelse på denne dag. Der er udeståender omkring afstemningsproceduren i den nyligt reviderede forordning nr. 1980/2000 af 17. juli 2000.
2. Formål og indhold
Formålet med den frivillige positive miljømærkeordning er at fremme udformningen, fremstillingen, markedsføringen og anvendelsen af produkter, som har mindsket indvirkning på miljøet gennem hele deres livscyklus samt give forbrugerne bedre information om produkters indvirkning på miljøet.
Nærværende beslutningsforslag indeholder kriterier for tildeling af miljømærket Blomsten til håndopvaskemidler. Kommissionen har, med Frankrig som ledende kompetent organ, udarbejdet forslaget. Undervejs i processen har repræsentanter for medlemslandene og interesseorganisationerne været hørt.
Definition af produktgruppen
Produktgruppen defineres som: Alle detergenter (opvaskemidler) som er beregnet til opvask i hånden af fade, porcelæn, bestik, skåle og andet køkkenudstyr.
Definitionen af produktgruppen og kriterierne for produktgruppen foreslås at gælde for en periode på 5 år regnet fra den første dag i den måned, der følger efter kommissionsbeslutningens ikrafttræden. Kommissionen ønsker nye kriterier fastsat 1 år før gyldigheden af de eksisterende ophører. Det vil i givet fald sige, at der skal foreligge nyt kriterieforslag igen om 4 år.
Kriterier
Der er kriterier for nedennævnte områder. De detaljerede krav kan ses i det vedlagte engelsksprogede kriterieforslag. "Nr." henviser til kriterieforslagets nummer.
|
Nr. |
Dansk |
Engelsk |
|
1 |
Giftighed overfor vandlevende organismer |
Toxicity to aquatic organisms |
|
2 |
Bionedbrydelighed af overfladeaktive stoffer", opdelt på 2a aerob og 2b anaerob nedbrydelighed, |
Biodegradability of surfactants 2a Ready biodegradability (aerobic), 2b Anaerobic biodegradability |
|
3 |
Farlige og giftige stoffer |
Dangerous, hazardous or toxic components |
|
4 |
Mangler (fejl i nummerering) |
- |
|
5 |
Parfumestoffer, opdelt på 5a Moskus-forbindelser og 5b Udvalgte parfumer |
Fragrances, 5a Musk, 5b Fragrances concerned |
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6 |
Farvestoffer |
Dyes or colouring agents |
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7 |
Biocider |
Biocides |
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8 |
Hud sensibilisering (overfølsomhed) |
Skin sensitisation |
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9 |
Mængde af overfladeaktive stoffer pr. vask |
Limitation of the total surfacatants per wash |
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10 |
Emballage |
Packaging requirements |
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11 |
Brugsegnethed |
Fitness for use |
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12 |
Forbrugerinformation |
User instructions |
3. Nærheds- og proportionalitetsprincippet
Kommissionen har ikke redegjort for nærheds- og proportionalitetsprincippet. Der er tale om en gennemførelsesforanstaltning af en allerede vedtaget rådsretsakt.
4. Forslagets konsekvenser for Danmark.
Lovgivningsmæssige konsekvenser
Forslaget medfører ingen lovgivningsmæssige konsekvenser for Danmark.
Økonomiske konsekvenser
Den europæiske miljømærkningsordning er frivillig. Erhvervelse af miljømærket indebærer udgifter for producenter og importører, men disse udgifter forventes opvejet af de konkurrencemæssige fordele ved anvendelsen af miljømærket. Forslaget forventes ikke at medføre statsfinancielle eller administrative konsekvenser.
Miljømæssige konsekvenser
Forslaget er første generation af kriterier for produktgruppen.
Miljøbelastningen fra de produkter, der kan tildeles licens, vil på grund af kravene være mindre end gennemsnittet for tilsvarende produkter. Forslaget forventes derfor at få miljøbeskyttelsesmæssigt positive konsekvenser, såfremt de miljømærkede produkter udbredes på markedet.
5. Høring
Forslaget har været i høring i Miljømærkenævnet. Her sidder repræsentanter for Dansk Industri, Det Danske Handelskammer, Dansk Handel & Service, Danmarks Naturfredningsforening, Forbrugerrådet, WWF Verdensnaturfonden i Danmark, LO, HK Industri, Forbrugerstyrelsen, Statens og Kommunernes Indkøbsservice, , Direktoratet for Arbejdstilsynet, to udvalgte detailhandelsrepræsentanter samt Miljø- og Energiministeriet v. Miljøst yrelsen. Nævnet var delt med hensyn til spørgsmålet om parfumestoffer. NGO{{PU2}}erne ønskede ikke parfumestoffer tilladt, industri- og handelsrepræsentanterne ønskede parfumestoffer tilladt.
Forslaget har desuden været i høring i EF-miljøspecialudvalget. Her indkom høringssvar fra Miljøkontrollen, SiD, Greenpeace.
Miljøkontrollen har ingen bemærkninger.
SiD mener at parfumestoffer (kriterie 5) ikke skal være tilladt i håndopvaskemidler.
Greenpeace har følgende bemærkninger:
Kriterie 3 Farlige og giftige stoffer: Ordlyden i forbudet mod "trichlorcarbon" bør bestemt formuleres bredere til "stoffer der indeholder aktivt chlor".
Kriterie 5b: Parfumestoffer bør ikke være tilladt. Greenpeace fremfører, at forbrugere, der køber miljømærkede produkter netop køber dem for at få noget, der er bedre for miljø og sundhed.
Kriterie 7 Biocider: Det er uacceptabelt at biocider, der er "meget giftige for organismer der lever i vand, samt kan forårsage uønskede langtidsvirkninger i vandmiljøet samt er giftige for organismer, der lever i vand" bliver tilladt i miljømærkede produkter.
Kriterie 8 Overfølsomhed: Hudsensibiliserende stoffer bør ikke tillades i mængder op til 1% i et miljømærket produkt.
Kriterie 10 Emballage: Det er uacceptabelt at der ikke er et direkte mod PVC i emballagen. PVC er forbudt i andre miljømærkede produkter. Dn fortsat aktiv fravælgelse af PVC hos producenterne bør fremmes.
ENV/2001/0043, draft 21 February 2001
COMMISSION DECISION ../{{NEL}}/EC
establishing the ecological criteria for the award of the Community eco-label to hand dishwashing detergents
COMMISSION DECISION ../{{NEL}}/EC
establishing the ecological criteria for the award of the Community eco-label to hand dishwashing detergents
(Text with EEA relevance)
(2001/--/---)
THE COMMISSION OF THE EUROPEAN COMMUNITIES,
Having regard to the Treaty establishing the European Community,
Having regard to Regulation (EC) No 1980/2000 of the European Parliament and of the Council of 17 July 2000 on a revised Community Eco-label award scheme, and in particular Articles 3, 4 and 6 thereof,
Whereas:
- Article 3 of Regulation (EC) No 1980/2000 provides that the eco-label may be awarded to a product possessing characteristics which enable it to contribute significantly to improvements in relation to key environmental aspects;
- Article 4 of Regulation (EC) No 1980/2000 provides that specific eco-label criteria shall be established according to product groups;
- the measures set out in this Decision have been developed and adopted under the procedures for the setting of eco-label criteria as laid down in Article 6 of Regulation (EC) No 1980/2000;
- the measures set out in this Decision are in accordance with the opinion of the committee set up under Article 17 of Regulation (EC) No 1980/2000,
HAS ADOPTED THIS DECISION:
Article 1
The product group {{PU1}}hand dishwashing detergents{{PU2}} (hereinafter referred to as {{PU1}}the product group{{PU2}}) shall mean:
"All detergents intended to be used to wash by hand dishes, crockery, cutlery, pots, pans and other kitchen utensils etc."
Article 2
The environmental performance and the fitness for use of the product group shall be assessed by reference to the criteria set out in the Annex.
Article 3
The product group definition and the criteria for the product group shall be valid for five years from the date on which this Decision takes effect.
Article 4
For administrative purposes the code number assigned to the product group shall be 019.
Article 5
This Decision is addressed to the Member States.
Done at Brussels,
For the Commission
Margot WALLSTRÖM
Member of the Commission
ANNEX
FRAMEWORK
In order to qualify for an eco-label, the product as defined in Article 1 must comply with the criteria of this Annex, with tests carried out on application as indicated in the criteria and the technical appendix. Where appropriate, other test methods may be used if their equivalence is accepted by the Competent Body assessing the application. Where no tests are mentioned, or are mentioned as being for use in verification or monitoring, Competent Bodies should rely as appropriate on decla rations and documentation provided by the applicant and/or independent verifications. Where it is indicated that specific documentation and/or declarations are required, these shall be provided by the applicant and/or the manufacturer(s) and/or the supplier(s) as appropriate.
The Competent Bodies are recommended to take into account the implementation of recognised environmental management schemes, such as EMAS or ISO 14001, when assessing applications and monitoring compliance with the criteria in this Annex (note: it is not required to implement such management schemes.)
These criteria aim in particular at promoting:
- the reduction of discharges of toxic or otherwise polluting substances into the aquatic environment,
- the reduction or prevention of risks to health or the environmental related to the use of hazardous substances
- the minimisation of packaging waste.
- information that will enable the consumer to use the product in the way that is efficient and minimises environmental impact
The criteria are set at levels that promote the labelling of hand dishwashing detergents that have a low environmental impact.
ECOLOGICAL CRITERIA
1. Toxicity to aquatic organisms
The critical dilution volume toxicity (CDVtox) is calculated for each ingredient (i) using the following equation:

where weight (i) is the weight of the ingredient per recommended dose for 1 litre of dishwashing water, LF is the loading factor and LTE is the long-term toxicity effect concentration of the ingredient.
The values of the LF and LTE parameters shall be as given in the Detergent Ingredient Database list (DID list) in appendix I A. If the ingredient in question is not included in the DID list, the applicant shall estimate their values following the approach described in appendix I B. The CDVtox is summed for each ingredient, making the CDVtox for the product.
The CDVtox of the recommended dose expressed for 1 litre of dishwashing water shall not exceed 130 litre.
The exact formulation of the product shall be provided, together with the details of the CDVtox calculations showing compliance with this criterion.
2. Biodegradability of Surfactants
a) Ready biodegradability (aerobic)
Each surfactant used in the product shall be readily biodegradable.
The tests for ready biodegradability shall be as referred to in Council Directive 67/548/EEC on the approximation of laws, regulations and administrative provisions relating to the classification, packaging and labelling of dangerous substances, and its subsequent amendments, in particular the methods detailed in Annex V.C4, or their equivalent OECD 301 A-F test methods, or their equivalent ISO tests. The 10 days window principle shall not apply. The pass levels shall be 70% for the te sts referred to in Annex V.C4-A and C.4-B of Directive 67/548/EEC (and their equivalent OECD 301 A and E tests and ISO equivalent), and shall be 60% for tests C4-C, D, E and F (and their equivalent OECD 301 B, F, D and C tests and ISO equivalents).
The exact formulation of the product shall be provided. For each surfactant, the results of the above-mentioned tests, or equivalent documentation from established literature, shall be provided.
b) Anaerobic Biodegradability
Each surfactant used in the product shall be biodegradable in anaerobic conditions.
The exact formulation of the product shall be provided. For each surfactant, the relevant information from the literature or other sources, or appropriate test results, shall be provided. The reference test for anaerobic degradability shall be ISO 11734, ECETOC N°. 28 (June 1988) or equivalent test method, with the requirement of a minimum of 60% degradability under anaerobic conditions.
3. Dangerous, hazardous or toxic components
a) The following ingredients shall not be included in the product, either as part of the formulation or as part of any preparation included in the formulation:
- alkyl phenol ethoxylates (APEOs),
- quaternary ammonium compounds
- trichlorocarbon
- formaldehyde
- EDTA (ethylene-diamine-tetra-acetate)
- NTA (nitrilo-tri-acetate)
- polyglycol solvents: polyethylene glycols
- Nitromusks and polycyclic musks, including for example:
Musk xylene: 5-tert-butyl-2,4,6-trinitro-m-xylene
Musk ambrette: 4-tert-butyl-3-methoxy-2,6-dinitrotoluene
Moskene: 1,1,3,3,5-pentamethyl-4,6-dinitroindan
Musk tibetine: 1-tert-butyl-3,4,5-trimethyl-2,6-dinitrobenzene
Musk ketone: 4{{PU2}}-tert-butyl-2{{PU2}},6{{PU2}}-dimethyl-3{{PU2}},5{{PU2}}-dinitroacetaphenone
HHCB (1,3,4,6,7,8-Hexahydro-4,6,6,7,8,8-hexamethylcyclopenta(g)-2-benzopyran)
AHTN (6-Acetyl-1,1,2,4,4,7-hexamethyltetralin)
b) No ingredient shall be included in the product that is classified as:
R40 (possible risks of irreversible effects),
R45 (may cause cancer),
R46 (may cause heritable genetic damage),
R49 (may cause cancer by inhalation),
R50+53 (very toxic to aquatic organism and may cause long term adverse effects in the aquatic environment),
R 51+53 (toxic to aquatic organism and may cause long term adverse effects in the aquatic environment),
R59 (dangerous to the ozone layer),
R60 (may impair fertility),
R61 (may cause harm to the unborn child),
R62 (possible risk of impaired fertility),
R63 (possible risk of harm to the unborn child),
R64 (may cause harm to breastfed babies),
or any combination thereof, according to Council Directive 67/548/EEC2 and its subsequent amendments.
Each ingredient of any preparation used in the formulation that exceeds 0.1% by weight of the preparation shall also meet the above requirement.
Biocides that are used as to preserve the product (as allowed under the criterion on biocides below), and that are classified as R50+53 or R51+53 are nevertheless permitted.
The exact formulation of the product shall be provided, together with copies of the Material Safety Data Sheets of each ingredient which shall indicate the classification or lack thereof of each ingredient, as well as a declaration that none of the above substances have been included in the product.
Similarly the suppliers of any preparation used in the formulation shall provide a declaration that their preparation complies with the above requirements.
5. Fragrances
a) The product shall not contain perfumes containing nitro-musks or polycyclic musks (as specified in the criterion above).
b) If the product contains one or more of the following fragrances, this shall be clearly indicated on the packaging, mentioning the name or names of the fragrances concerned:
Common name CAS n° Common name CAS n°
Amyl cinnamal 122-40-7 Amylcinnamyl alcohol 101-85-9
Benzyl alcohol 100-51-6 Benzyl salicylate 118-58-1
Cinnamyl alcohol 104-54-1 Cinnamal 104-55-2
Citral 5392-40-5 Coumarin 91-64-5
Eugenol 97-53-0 Geraniol 106-24-1
Hydroxycitronellal 107-75-5 Hydroxymethyl 31906-04-4
Isoeugenol 97-54-1 penthylcyclohexenrcarboxaldehyde
c) Any ingredients added to the product as a fragrance must have been manufactured and/or handled following the code of practice of the International Fragrance Association.
A declaration of compliance with each part of this criterion shall be provided.
6. Dyes or colouring agents
Any dyes or colouring agents used in the product must be permitted by Council Directive 76/768/EEC of on the approximation of the laws of the Member States relating to cosmetic products and its subsequent amendments, and must be permitted by European Parliament and Council Directive 94/36/EEC of 30 June 1994 on colours for use in foodstuffs and its subsequent amendments.
A declaration of compliance with this criterion shall be provided, together with a full list of all dyes used.
7. Biocides
a) The product may only include biocides in order to preserve the product, and in the appropriate dosage for this purpose alone. This does not refer to surfactants which may also have biocidal properties.
The exact formulation of the product shall be provided, together with copies of the Material Safety Data Sheets of any preservatives added, as well as information on the dosage necessary to preserve the product. A declaration of compliance with this criterion shall be provided.
b) It is prohibited to claim or suggest on the packaging or by any other communication that the hand dishwashing product has an antimicrobial action.
The texts and layouts used on each packaging and/or an example of each different packaging shall be provided, together with a declaration of compliance with this criterion.
8. Skin sensitisation
No ingredient classified as R42 (may cause sensitization by inhalation) and/or R43 (may cause sensitization by skin contact) according to Council Directive 67/548/EEC and its subsequent amendments shall exceed 1% by weight of the total undiluted product.
The exact formulation of the product shall be provided, together with copies of the Material Safety Data Sheets of each ingredient which shall indicate the classification or lack thereof of each ingredient. A declaration of compliance with this criterion shall also be provided.
9. Limitation of the total surfacatants per wash
The weight of total surfactants in the recommended dose for 1 litre of dishwashing water shall not exceed 0.4 g for dirty dishes.
Data on the total active matter per ml of product shall be provided, together with the recommended dosage in ml for 1l of dishwashing water for dirty dishes that appears on the packaging. On the basis of this data, compliance with this criterion shall be demonstrated.
10. Packaging requirements
a) The primary packaging shall have a volumetric coefficient of packaging (VCP) less than or equal to 1.9. This criterion does not apply if the primary packaging is made up of 50% or more recycled material.
VCP is equal to the volume of the smallest rectangular solid (rectangular parallelepiped) that can contain the packaging divided by the volume of the product contained in the packaging.
b) If the primary packaging is made of recycled material, any indication of this on the packaging shall be in conformity with the ISO 14021 standard "Environmental labels and declarations {{SPA}} Self declared claims (type II environmental labelling)".
c) The primary packaging parts shall be easily separable into mono-material parts.
Data on the packaging, and/or a sample thereof if appropriate, shall be provided, together with a declaration of compliance with this criterion.
FITNESS FOR USE
11. Fitness for use
The product shall be fit for use, meeting the needs of the consumers.
All relevant data shall be provided. This shall at least include the results of a performance test comparing the product (at the recommended dosage, tested on dirty dishes) with water and with at least one other product (commonly available in the area where the eco-labelled product is to be marketed, and at its recommended dosage). The choice of the reference product(s) and test protocol used for these comparisons shall be justified.
CONSUMER INFORMATION
12. User instructions
The product shall bear the following information on the packaging:
a) "To wash your dishes in the most efficient way, to save water and energy, and to protect the environment, do not use running water but immerse the dishes, and use the recommended dosage. You can wash most efficiently without lots of foam" (or equivalent text).
b) The pictogram and information below shall appear on the packaging in a reasonably sufficient size and against a visible background:
Recommended dosage for 5 litres of dishwashing water :
not very dirty x ml (y tea spoons) of product
dirty z ml (w tea spoons) of product
where x, y, z and w have to be defined by the applicant and/or the manufacturer.
The metric used in the above pictogram shall be millilitres. A second well-known metric, such as teaspoons, shall additionally be given in brackets (as in the pictogram above). However, if the packaging has an efficient and convenient dosing system that can provide an equally reliable dosage, an alternative metric (e.g. capfulls, squirts, or other) may be used.
c) An indication of the approximate number of washes that the consumer can perform with one bottle.
This is calculated by dividing the volume of the product by the dosage required for 5l of dishwashing detergent for dirty dishes (as indicated in the pictogram above).
d) Commission Recommendation 89/542/EEC of 13 September 1989 for the labelling of detergents and cleaning products shall to be applied.
e) If the product contains perfumes, this shall be indicated on the packaging.
f) "For more information visit the EU Eco-label web-site: http://europa.eu.int/ecolabel" (or equivalent text).
A sample of the product packaging, including the label, shall be provided, together with a declaration of compliance with each part of this criterion.
13. Information appearing on the eco-label
Box 2 of the eco-label shall contain the following text:
* reduced environmental impact
* clear dosage instructions
Appendix i
Detergents Ingredients database and approach to be follwed for ingredients not listed in the database
A. Detergent Ingredients Database (DID-list; version 29.09.98)
|
DID |
Ingredients |
Toxicity |
Loading |
Anaerobic Non-Bio- |
Aerobic Non-Bio- |
Soluble |
Insoluble |
||
|
No |
NOEC measured |
LTE |
factor (LF) |
degradable (an NBO) |
degradable (a NBO) |
Inorganics (SI) |
Inorganics ( II) |
THOD |
|
|
Anionic surfactants |
|||||||||
|
1 |
C 10-13 LAS (Na ø 11.5-11.8. C14<1 %) |
0.3 |
0.3 |
0.05 |
Y, CF = 0.75 |
O |
O |
O |
2.3 |
|
2 |
other LAS (C14 > 1 %) |
0.12 |
0.12 |
0.05 |
Y, CF = 1.5 |
O |
O |
O |
2.3 |
|
3 |
C 14/17 alk. sulfonate |
0.27 |
0.27 |
0.03 |
Y, CF = 0.75 |
O |
O |
O |
2.5 |
|
4 |
C 8/10 Alkylsulfate |
EC50= 2.9 |
0.15 |
0.02 |
O |
O |
O |
O |
1.9 |
|
5 |
C 12-15 AS |
0.1 |
0.1 |
0.02 |
O |
O |
O |
O |
2.2 |
|
6 |
C 12-18 AS |
LC50 = 3 |
0.15 |
0.02 |
O |
O |
O |
O |
2.3 |
|
7 |
C 16/18 FAS |
0.55 |
0.55 |
0.02 |
O |
O |
O |
O |
2.5 |
|
8 |
C 12-15 A 1-3 EO sulphate |
0.15 |
0.15 |
0.03 |
O |
O |
O |
O |
2.1 |
|
9 |
C 16/18 A 3-4 EO sulphate |
no valid data |
0.1 |
0.03 |
O |
O |
O |
O |
2.2 |
|
10 |
C 8 -Dialkylsulfosuccinate |
LC50 = 7.5 |
0.4 |
0.5 |
Y, CF = 1.5 |
O |
O |
O |
2 |
|
11 |
C 12/14 sulpho-fat.-acid methylester |
EC50 = 5 |
0.25 |
0.05 |
Y, CF = 0.75 |
O |
O |
O |
2.1 |
|
12 |
C 16/18 sulpho-fat.-acid methylester |
0.15 |
0.15 |
0.05 |
Y, CF = 0.75 |
O |
O |
O |
2.3 |
|
13 |
C 14/16 alpha olefine sulphonate |
LC50 = 2.5 |
0.13 |
0.05 |
Y, CF = 0.75 |
O |
O |
O |
2.3 |
|
14 |
C 14-18 alpha olefine sulphonate |
LC50 = 1.4 |
0.07 |
0.05 |
Y, CF = 2.0 |
O |
O |
O |
2.4 |
|
15 |
soaps (C12 - 22) |
EC0 = 1.6 |
1.6 |
0.05 |
O |
O |
O |
O |
2.9 |
|
Nonionic surfactants |
|||||||||
|
16 |
C 9/11 A >3-6 EO lin. or mono br. |
EC50=3.3 |
0.7 |
0.03 |
O |
O |
O |
O |
2.4 |
|
17 |
C 9/11 A > 6-9 EO lin. or mono br. |
EC50=5.4 |
1.1 |
0.03 |
O |
O |
O |
O |
2.2 |
|
18 |
C 12-15 A 2-6 EO lin. or mono br. |
0.18 |
0.18 |
0.03 |
O |
O |
O |
O |
2.5 |
|
19 |
C 12-15 (Avg. C<14) A >6-9 EO lin. or mono br. |
0.24 |
0.24 |
0.03 |
O |
O |
O |
O |
2.3 |
|
20 |
C 12-15 (Avg. C>14) A >6-9 EO |
0.17 |
0.17 |
0.03 |
O |
O |
O |
O |
2.3 |
|
21 |
C 12-15 A >9-12 EO |
LC50 = 0.8 |
0.3 |
0.03 |
O |
O |
O |
O |
2.2 |
|
22 |
C 12-15 A 20-30 EO |
EC50 = 13 |
0.65 |
0.05 |
O |
O |
O |
O |
2 |
|
23 |
C 12-15 A > 30 EO |
LC50 = 130 |
6.5 |
0.75 |
O |
Y |
O |
O |
0* |
|
24 |
C 12/18 A 0-3 EO |
no data |
0.01 |
0.03 |
O |
O |
O |
O |
2.9 |
|
25 |
C 12-18 A 9 EO |
0.2 |
0.2 |
0.03 |
O |
O |
O |
O |
2.4 |
|
26 |
C 16/18 A 2-6 EO |
0.03 |
0.03 |
0.03 |
O |
O |
O |
O |
2.6 |
|
27 |
C 16/18 A > 9-12 EO |
LC50 = 0.5 |
0.05 |
0.03 |
O |
O |
O |
O |
2.3 |
|
28 |
C 16/18 A 20-30 EO |
EC50 = 18 |
0.36 |
0.05 |
O |
O |
O |
O |
2.1 |
|
29 |
C 16/18 A > 30 EO |
LC50 = 50 |
2.5 |
0.75 |
O |
Y |
O |
O |
0* |
|
30 |
C 12/14 Glucose Amide |
4.3 |
4.3 |
0.03 |
O |
O |
O |
O |
2.2 |
|
31 |
C 16/18 Glucose Amide |
0.116 |
0.116 |
0.03 |
O |
O |
O |
O |
2.5 |
|
32 |
C 12/14 Alkylpolyglucoside |
1 |
1 |
0.03 |
O |
O |
O |
O |
2.3 |
|
Amphoteric surfactants |
|||||||||
|
33 |
C 12-15 Alkyl dimethylbetaine |
0.03 |
0.03 |
0.05 |
Y, CF= 2.5 |
O |
O |
O |
2.9 |
|
34 |
C12-18 Alkyl amidopropylbetaine |
0.03 |
0.03 |
0.05 |
Y,CF = 2.5 |
O |
O |
O |
2.8 |
|
Sud controllers |
|||||||||
|
35 |
silicone |
EC0 = 241 |
4.82 |
0.4 |
Y,CF = 0.75 |
Y |
O |
O |
0.0 |
|
36 |
paraffin |
no data |
100 |
0.4 |
O |
Y |
O |
O |
0* |
|
Fabric Softening |
|||||||||
|
37 |
Glycerol |
LC50 > 5-10 gl |
1000 |
0.13 |
O |
O |
O |
O |
1.2 |
|
Builders |
|||||||||
|
38 |
phosphate as STPP |
1000 |
0.6 |
O |
O |
Y |
O |
0.0 |
|
|
39 |
zeolite A |
120 |
120 |
0.05 |
O |
O |
O |
Y |
0.0 |
|
40 |
citrate |
EC50 = 85 |
85 |
0.07 |
O |
O |
O |
O |
0.6 |
|
41 |
polycarboxylates and related derivates |
124 |
124 |
0.4 |
Y, CF = 0.1 |
Y |
O |
O |
0* |
|
42 |
clay |
1000 |
0.05 |
O |
O |
O |
Y |
0.0 |
|
|
43 |
carbonate /bicarbonate |
LC50 = 250 |
250 |
0.8 |
O |
O |
Y |
O |
0.0 |
|
44 |
fatty acid (C >=14) |
EC0=1.6 |
1.6 |
0.05 |
O |
O |
O |
O |
2.9 |
|
45 |
silicate |
EC50 > 1000 |
1000 |
0.8 |
O |
O |
Y |
O |
0.0 |
|
46 |
NTA |
19 |
19 |
0.13 |
O |
O |
O |
O |
0.6 |
|
47 |
Polyaspartic acid. Na salt |
125 |
12.5 |
0.13 |
Y,. CF=0.1 |
O |
O |
O |
1.2 |
|
Bleaching |
|||||||||
|
48 |
perborate mono (as borate) |
1 - 10 |
6 |
1 |
O |
O |
Y |
O |
0.0 |
|
49 |
perborate tetra (as borate) |
1 - 10 |
6 |
1 |
O |
O |
Y |
O |
0.0 |
|
50 |
percarbonate (see carbonate) |
LC50 = 250 |
250 |
0.8 |
O |
O |
Y |
O |
0.0 |
|
51 |
TAED |
EC0 = 500 |
EC0 = 500 |
0.13 |
O |
O |
O |
O |
2.0 |
|
Solvents |
|||||||||
|
52 |
C 1-C4 alcohols |
LC50 = 8000 |
100 |
0.13 |
O |
O |
O |
O |
2.3 |
|
53 |
Monoethanolamine |
0.78 |
0.78 |
0.13 |
O |
O |
O |
O |
2.4 |
|
54 |
Diethanolamine |
0.78 |
0.78 |
0.13 |
O |
O |
O |
O |
2.3 |
|
55 |
Triethanolamine |
0.78 |
0.78 |
0.13 |
O |
O |
O |
O |
2 |
|
Miscellaneous |
|||||||||
|
56 |
Polyvinylpyrrolidon PVP / PVNO / PVPVI |
EC50 > 100 |
100 |
0.75 |
Y, CF = 0.1 |
Y |
O |
O |
0* |
|
57 |
Phosphonates |
7.4 |
7 |
0.4 |
Y, CF = 0.5 |
Y |
O |
O |
0* |
|
58 |
EDTA |
LOEC = 11 |
11 |
1 |
Y, CF = 0.1 |
Y |
O |
O |
0* |
|
59 |
CMC |
LC50 > 250 |
250 |
0.75 |
Y, CF = 0.1 |
Y |
O |
O |
0* |
|
60 |
Na sulphate |
EC50 = 2460 |
1000 |
1 |
O |
O |
Y |
O |
0.0 |
|
61 |
Mg Sulphate |
EC50 = 788 |
800 |
1 |
O |
O |
Y |
O |
0.0 |
|
62 |
Na chloride |
EC50 = 650 |
650 |
1 |
O |
O |
Y |
O |
0.0 |
|
63 |
urea |
LC50>10000 |
100 |
0.13 |
O |
O |
O |
O |
2.1 |
|
64 |
maleic acid |
LC50 = 106 |
2.1 |
0.13 |
O |
O |
O |
O |
0.8 |
|
65 |
malic acid |
LC50 = 106 |
2.1 |
0.13 |
O |
O |
O |
O |
0.6 |
|
66 |
Ca formiate |
100 |
0.13 |
O |
O |
O |
O |
2.0 |
|
|
67 |
Silica |
100 |
0.05 |
O |
O |
O |
Y |
0.0 |
|
|
68 |
High MW polymers PEG > 4000 |
100 |
0.4 |
O |
Y |
O |
O |
0* |
|
|
69 |
Low MW polymers PEG < 4000 |
100 |
0.13 |
O |
O |
O |
O |
1.1 |
|
|
70 |
cumenesulfonate |
LC50 = 66 |
6.6 |
0.13 |
Y, CF = 0.25 |
O |
O |
O |
1.7 |
|
71 |
xylenesulfonate |
LC50 = 66 |
6.6 |
0.13 |
Y, CF = 0.25 |
O |
O |
O |
1.6 |
|
72 |
toluene sulfonates |
LC50 = 66 |
6.6 |
0.13 |
Y, CF = 0.25 |
O |
O |
O |
1.4 |
|
73 |
Na-/Mg-/KOH |
100 |
1 |
O |
O |
Y |
O |
0.0 |
|
|
74 |
enzymes |
LC50 = 25 |
25 |
0.13 |
O |
O |
O |
O |
2.0 |
|
75 |
perfume formulation as used |
LC50 = 2-10 |
0.02 |
0.1 |
Y, CF = 3.0 |
Y |
O |
O |
0* |
|
76 |
dyes |
LC50 = 10 |
0.1 |
0.4 |
Y, CF = 3.0 |
Y |
O |
O |
0* |
|
77 |
Starch |
no data |
250 |
0.1 |
O |
O |
O |
O |
0.97 |
|
78 |
Zn Phthalocyanine Sulfonate |
0.16 |
0.016 |
0.07** |
Y, CF=2.5 |
Y |
O |
O |
0* |
|
79 |
Anionic Polyester (Soil release polymer) |
EC50=310 |
310 |
0.4 |
Y,CF=0.1 |
Y |
O |
O |
0* |
|
80 |
Iminodisuccinate |
23 |
2.3 |
0.13 |
Y,CF=0.25 |
O |
O |
O |
1.1 |
|
Optical brighteners = FWA |
|||||||||
|
81 |
FWA 1 1 |
LC0 = 10 |
1.0 |
0.4 |
Y, CF = 1.5 |
Y |
O |
O |
0* |
|
82 |
FWA 5 2 |
3.13 |
3.13 |
0.4 |
Y, CF = 0.5 |
Y |
O |
O |
0* |
|
Additional ingredients |
|||||||||
|
83 |
C12-18 Alkyl Aminoxides |
0.08 |
0.08 |
0.05 |
Y,CF = 2.5 |
O |
O |
O |
3.2 |
|
84 |
Glycereth (6-17EO) cocoate |
EC50=32 |
1.6 |
0.05 |
O |
O |
O |
O |
2.1 |
|
85 |
C12-18 Phosphate esters |
EC50=38 |
1.9 |
0.05 |
Y,CF = 0.25 |
O |
O |
O |
2.3 |
1
FWA 1 = Disodium 4.4'-bis (4-anilino-5-morpholino-1.3.5-triazin-2-yl)amino stilbene-2.2'-disulfonate.2
FWA 5 = Disodium 4.4'-bis(2-sulfostryryl)biphenyl.0* THOD for aerobically non degradable organic substances is set to zero.
**
rapid photodegradationNotes:
NOEC = non observed effect concentration CF = correction factor for anaerobic non degradable substances
LTE = long term toxicity effect concentration THOD = Theoretical oxygen demand Remark:
Y = yes, criterion applies a NBO, SI, II, THOD are not used in the criteria for this product group
0 = no, criterion does not apply
B. Approach for ingredients which are not included in the DID-list
For ingredients which are not included in the DID-list, the applicant shall assess the data for criteria calculating in own responsibility. The reference for the relevant tests shall be the appropriate annexes of council directive 67/548/EC. For assessing data for ingredients which are not in the DID-list the applicant may use existing Chemical Databases such as IUCLD (International Uniform Chemical Database for the Implementation of Council Regulat ion EEC 793/93).
The approach for estimating long-term-toxicity effect concentration (LTE) and loading factors (LF) is given below.
1) How to estimate long-term-toxicity-effect concentration (LTE)
As LTE the lowest validated long term toxicity concentration for fish, daphnia magna or algae shall be considered.
In cases where data on homologues and/or QSARs (Quantitative Structure Activity Relationships) are used, a correction could be considered for the finally selected LTE data. If long term toxicity data (such as NOEC) for one or more of the three species are missing, or only short term toxicity data (such as LC50) are available, the following uncertainty factors (UF) shall be used:
1-1) Uncertainty factors (UF) for non-surfactants
data available UF to be used
3 NOEC on fish, daphnia or algae 1 (take lowest validated NOEC)
2 NOEC on fish or daphnia or algae 5
1 NOEC on fish or daphnia or algae 10
At least 2 acute LC50 on fish or daphnia or algae 100
Deviation from this rule may be admitted if evidence can be provided that lower factors or data can be scientifically justified.
1-2) Uncertainity factors (UF) for surfactants
data available UF to be used
At least 2 NOECs on fish or daphnia or algae 1 (lowest NOEC)
1 NOEC on fish or daphnia or algae 1 (if species is most sensitive in acute toxicity)
10 (if species is not the most sensitive in acute toxicity)
3 LC50 on fish or daphnia or algae 20 (lowest LC50)
At least 1 LC50 on fish, daphnia or algae 50 (lowest LC50) or 20 in specific cases *
* In the last case referred to above, an uncertainty factor of 20 may be used instead of 50 only if 1-2 L(E)C50 (LC 50 in case of fish toxicity, EC50 in case of daphnia magna and algae toxicity) data are available and if it can be concluded from the information for other compounds that the most sensitive species have been tested. Such a rule can be applied only within a group of homologues. It is emphasised that the LTEs (long-term effects) used must be consistent within a group of homologues with respect to the influence of e.g. length of alkyl chain for LAS (linear alkylbenzene sulphonate) or number of EOs (ethoxy groups) for alcohol-ethoxylate. Any deviation from the scheme described above shall be well reasoned for the specific chemical.
2) How to estimate Loading factors (LF)
The loading factors (LF) for calculating the Critical dilution volume toxicity (CDVtox) reflect the bio-degradability of the substance.
2-1) Loading factors for organic substances
Degradability of substance sorption loading factor (LF)
Ready biodegradable Low 0.13
Medium 0.1
High 0.07
Inherent biodegradable Low 0.6
Medium 0.5
High 0.3
Non-biodegradable Low 1
Medium 0.75
High 0.4
Note: Sorption can be estimated by log POW (Partition Coefficient Octanol/Water), where POW <2 is seen as "low sorption, POW 2
2-2) Special approach for readily degradable surfactants
Type of surfactant Loading factor (LF) to be used
Readily degradable surfactants in general 0.05
Alcohol ethoxylates (EO < 20) & Alcohol ethoxysulfates 0.03
Alcohol sulphates 0.02
2-3) Special approach for inorganic substances
Type of INorganic substance Loading factor (LF) to be used
soluble inorganic substances 1
insoluble inorganic substances 0.05