2003/31/EC: Commission Decision of 29 November 2002 establishing revised ecological criteria for the award of the Community eco-label to detergents for dishwashers and amending Decision 1999/427/EC (Text with EEA relevance) (notified under document number C(2002) 4632)
Date: 2002-11-29
Institutions: European Commission
Subjects: consumer information, eco-label, ecology, household electrical appliance, polishing and scouring preparations, product quality

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II

(Acts whose publication is not obligatory)

COMMISSION

COMMISSION DECISION

of 29 November 2002

establishing revised ecological criteria for the award of the Community eco-label to detergents for
dishwashers and amending Decision 1999/427/EC

(notified under document number C(2002) 4632)

(Text with EEA relevance)

(2003/31/EC)

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 (1), and in parti-
cular the second subparagraph of Article 6(1) thereof,

Whereas:

(1)

(2)

(3)

(4)

Under Regulation (EC) No 1980/2000 the Community
eco-label may be awarded to a product possessing char-
acteristics which enable it to contribute significantly to
improvements in relation to key environmental aspects.

Regulation (EC) No 1980/2000 provides that specific
eco-label criteria are to be established according to
product groups.

It also provides that the review of the eco-label criteria,
as well as of the assessment and verification require-
ments related to the criteria, is to take place in due time
before the end of the period of validity of the criteria
specified for each product group.

It is appropriate to revise the ecological criteria that were
established by Commission Decision 1999/427/EC of 28
May 1999 establishing the ecological criteria for the
award of the Community eco-label
to detergents for
dishwashers (2), in order to reflect the developments in
the market. At the same time, the period of validity of
that Decision as extended by Decision 2002/173/EC (3)
and the definition of the product group should be modi-
fied.

(1) OJ L 237, 21.9.2000, p. 1.
(2) OJ L 167, 2.7.1999, p. 38.
(3) OJ L 56, 27.2.2002, p. 33.

(5)

(6)

(7)

(8)

A new Decision should be adopted establishing the
specific ecological criteria for this product group, which
will be valid for a period of five years.

It is appropriate that, for a limited period of not more
than 18 months, both the new criteria and the criteria
established by Decision 1999/427/EC should be valid
concurrently,
time for
companies that have been awarded or that have applied
for the award of the eco-label for their products prior to
the date of application of this Decision, to adapt those
products to comply with the new criteria.

to allow sufficient

in order

The measures provided for in this Decision are based on
the draft criteria developed by the European Union Eco-
Labelling Board established under Article 13 of Regula-
tion (EC) No 1980/2000.

The measures provided for in this Decision are in accor-
dance with the opinion of the Committee instituted by
Article 17 of Regulation (EC) No 1980/2000,

HAS ADOPTED THIS DECISION:

Article 1

In order to be awarded the Community eco-label under Regula-
tion (EC) No 1980/2000, a detergent for dishwashers must fall
within the product group ‘detergents
for dishwashers’ as
defined in Article 2, and must comply with the ecological
criteria set out in the Annex to this Decision.

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Article 2

Article 5

The product group ‘detergents for dishwashers’ shall comprise
all detergents
intended for use exclusively in automatic
domestic dishwashers and all detergents intended for use in
automatic dishwashers operated by professional users but
similar to automatic domestic dishwashers in terms of machine
size and usage.

Article 3

For administrative purposes the code number assigned to the
product group ‘detergents for dishwashers’ shall be ‘015’.

This Decision shall apply from 1 January 2003 until 31
December 2007.

Producers of products falling within the product group ‘deter-
gents for dishwashers’ which have already been awarded the
eco-label before 1 January 2003 may continue to use that label
until 31 May 2004.

Producers of products falling within the product group ‘deter-
gents for dishwashers’ which have already applied for the
award of the eco-label before 1 January 2003 may be awarded
the eco-label under the terms of Decision 1999/427/EC. In
these cases the label may be used until 31 May 2004.

Article 4

This Decision is addressed to the Member States.

Article 6

Article 3 of Decision 1999/427/EC is
following:

replaced by the

‘Article 3

The product group definition and the specific ecological
criteria for the product group shall be valid until 31 May
2004.’

Done at Brussels, 29 November 2002.

For the Commission

Margot WALLSTRÖM

Member of the Commission

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ANNEX

FRAMEWORK

The aims of the criteria

These criteria aim in particular at promoting:

— reduction of water pollution both by reducing the quantity of detergent used and by limiting the quantity of harmful

ingredients,

— reduction of energy use by promoting low temperature detergents,

— the minimisation of waste by reducing the amount of primary packaging.

Additionally, the criteria enhance the consumers' environmental awareness. The criteria are set at levels that promote the
labelling of detergents for dishwashers that have a low environmental

impact.

The specific assessment and verification requirements are indicated within each criterion.

Assessment and verification requirements

Where the applicant is required to provide declarations, documentation, analyses, test reports, or other evidence to show
compliance with the criteria, it is understood that these may originate from the applicant and/or his supplier(s) and/or
their supplier(s), et cetera, as appropriate.

Where possible, the testing should be performed by laboratories that meet the general requirements of EN ISO 17025 or
equivalent.

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 verifica-
tions.

Where appropriate, the applicant may use subsequent revisions of the Detergent Ingredient Database as they become
available.

The competent bodies are recommended to take into account the implementation of recognised environmental manage-
ment schemes, such as EMAS or ISO14001, when assessing applications and monitoring compliance with the criteria
(note:

it is not required to implement such management schemes.).

Functional unit and reference dosage

The functional unit, to which inputs and outputs should be related, shall be the quantity of product required to wash 12
place settings with a standard soil (as defined by DIN or ISO standards). The dosage recommended by the manufacturer to
consumers for normally soiled dishes and 12 place settings is taken as a reference dosage under standard conditions, as
laid down in the IKW washing performance test referred to in criterion 6.

CRITERIA

1. Environmental scoring matrix

The following five parameters are included in an environmental matrix and are aggregated and assessed as a whole, as
presented below:

— total chemicals,

— critical dilution volume, toxicity (CDVtox),

— phosphates (expressed as sodium tripolyphosphate — STPP),

— aerobic non-biodegradable organics (aNBDO),

— anaerobic non-biodegradable organics (anNBDO).

The following table summarises these parameters and their related scoring, their exclusion hurdles and their weighting
factors. The formulae for calculating the score for each parameter and the exclusion hurdles are detailed below in points
(a) to (f). The parameters are calculated for each ingredient by considering the dosage per wash, water content and mass
percentage in the formulation and they are added up for each product formulation.

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Parameter

Total chemicals

Critical dilution volume,

toxicity

Phosphates (as STPP)

Aerobically non-biodegradable
organics

Anaerobically
able organics

non-biodegrad-

Environmental scoring matrix

Score

3

18

120

2,5

0,25

0,05

4

19,5

180

5

0,5

0,10

4

16,5

60

0

0

0

1

21

7,5

0,75

0,15

Excluding
hurdle

Weight
factor

22,5

200

10

1

3

8

2

1

0,2

1,5

Minimum score required

30

Note: All values are expressed in g/wash, except CDVtox which is expressed in l/wash.

Assessment and verification: The exact formulation of the product shall be provided,
including the exact chemical
description of ingredients (e.g. identification according to IUPAC, CAS No, sum and structural formulae, purity, type and
percentage of impurities, additives; for mixtures, e.g. surfactants: DID number, composition and spectrum of distribution
homologues, isomers, and trade names); analytical evidence of the composition of surfactants, and the exact tonnage of
product that is put on the market (reporting on 1 March, related to the year before).

(a) 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, LF is the loading factor and LTE is the
long-term toxicity effect concentration of the ingredient. The CDVtox is summed for each ingredient (i), making the
CDVtox for the product:

CDVtox shall be ≤ 200 l/wash.

Score (CDVtox) = (5 – (CDVtox/60)) × 8

Assessment and verification: The exact formulation of the product shall be provided to the Competent Body, together
ingredients included in the Detergent
with the details of the CDVtox calculations and the related score. For all
Ingredient Database (DID-list, see Annex IA), the relevant values given in the DID-list shall be used, and the
corresponding ingredient number shall be given. In the case of new chemicals or additional ingredients that are not
listed in the DID list the approach described in Appendix I.B shall be followed.

(b) Total chemicals

Total chemicals,

in g/wash, are the recommended dosage minus water content.

Total chemicals shall be ≤ 22,5 g/wash.

Score (Total chemicals) = (15 – (Total chemicals/1,5)) × 3

Assessment and verification: The exact formulation of the product shall be provided to the competent body, together
with the details of the total chemical calculations and the related score.

(c) Phosphates (as STPP — sodium tripolyphosphate)

Phosphates are the quantity of phosphates in the formulation calculated as STPP.

Phosphates shall be ≤ 10 g/wash.

Score (Phosphates) = (4 – (Phosphates/2,5)) × 2

Assessment and verification: The exact formulation of the product shall be provided to the Competent Body, together
with the details of phosphate calculations and the related score.

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(d) Aerobically non-biodegradable organics (aNBDO)

Aerobically non-biodegradable organics is the weight per wash,
aerobically non-biodegradable (see DID-list).

in g/wash, of all organic ingredients which are

aNBDO shall be ≤ 1 g/wash

Score(aNBDO) = 4 – (aNBDO/0,25)

Assessment and verification: The exact formulation of the product shall be provided to the competent body, together
with the details of the aNBDO calculations and the related score. For all ingredients included in the DID-list (Annex
IA), the relevant data given in the DID-list shall be used. For ingredients which are not included in the DID list, the
relevant information from literature or other sources, or appropriate test results, showing that they are aerobically
biodegradable shall be provided. The tests for ready biodegradability shall be as referred to in Council Directive
67/548/EEC of 27 June 1967 on the approximation of laws, regulations and administrative provisions relating to the
classification, packaging and labelling of dangerous substances (1), 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 tests referred to in Annex V.C4-A and
C4-B of Directive 67/548/EEC (and their equivalent OECD 301 A and E tests and ISO equivalents), and shall be 60 %
for tests C4-C, D, E and F (and their equivalent OECD 301 B, C, D and F tests and ISO equivalents).

(e) Anaerobically non-biodegradable organics (anNBDO)

Anaerobically non-biodegradable organics is the weight per wash,
anaerobically non-biodegradable using respective correction factors (see DID-list).

in g/wash, of all organic ingredients that are

anNBDO shall be ≤ 0,2 g/wash.

Score(anNBDO) = (4 – (anNBDO/0,05)) × 1,5

Assessment and verification: The exact formulation of the product shall be provided to the Competent Body, together
with the details of the anNBDO calculations and the related score. For all ingredients included in the DID-list (Annex
IA), the relevant data given in the DID-list shall be used. For ingredients which are not included in the DID list, the
relevant information from literature or other sources, or appropriate test results, showing that they are anaerobically
biodegradable shall be provided. The reference test for anaerobic degradability shall be ISO 11734, ECETOC No 28
(June 1988) or an equivalent test method, with the requirement of 60 % ultimate degradability under anaerobic
conditions. Test methods simulating the conditions in a relevant anaerobic environment may also be used to
document that 60 % ultimate degradability has been attained under anaerobic conditions (see Appendix IC).

(f) Total score

The sum of Score (CDVtox) + Score (Total chemicals) + Score (Phosphates) + Score (aNBDO) + Score (anNBDO) shall be
≥ 30.

Assessment and verification: The exact formulation of the product shall be provided to the Competent Body, together
with the details of the total score calculations.

2. Biodegradability of surfactants

(a) Ready aerobic biodegradability

Each surfactant used in the product shall be readily biodegradable.

Assessment and verification: The exact formulation of the product shall be provided to the competent body. The DID list
(see Appendix IA) indicates whether a specific surfactant is aerobically biodegradable or not (i.e. those that have an
entry of ‘Y’ in the column on aerobic biodegradability shall not be used). For surfactants which are not included in the
DID list, the relevant information from literature or other sources, or appropriate test results, showing that they are
aerobically biodegradable shall be provided. The tests for ready biodegradability shall be as referred to in Directive
67/548/EEC, 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 tests referred to in Annex V.C4-A and C4-B of Directive 67/548/EEC (and their equivalent
OECD 301 A and E tests and ISO equivalents), and shall be 60 % for tests C4-C, D, E and F (and their equivalent
OECD 301 B, C, D and F tests and ISO equivalents).

(1) OJ 196, 16.8.1967, p. 1.

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(b) Anaerobic biodegradability

Each surfactant used in the product shall be anaerobically biodegradable.

Assessment and verification: The exact formulation of the product shall be provided. The DID list (see Appendix IA)
indicates whether a specific surfactant is anaerobically biodegradable or not (i.e. those that have an entry of ‘Y’ in the
column on anaerobic biodegradability shall not be used). For surfactants which are not included in the DID list, the
relevant information from literature or other sources, or appropriate test results, showing that they are anaerobically
biodegradable shall be provided. The reference test for anaerobic degradability shall be ISO 11734, Ecetoc No 28
(June 1988) or an equivalent test method, with the requirement of 60 % ultimate degradability under anaerobic
conditions. Test methods simulating the conditions in a relevant anaerobic environment may also be used to
document that 60 % ultimate degradability has been attained under anaerobic conditions (see Appendix IC).

3. Dangerous, hazardous or toxic substances or preparations

(a) No ingredient shall be included in the product that, at the time of application, is or may be assigned any of the

following risk phrases (or combinations thereof):

R40

R45

R46

R49

(limited evidence of a carcinogenic effect)

(may cause cancer)

(may cause heritable genetic damage)

(may cause cancer by inhalation)

R50-53 (very toxic to aquatic organisms and may cause long-term adverse effects in the aquatic environment)

R51-53 (toxic to aquatic organisms and may cause long-term adverse effects in the aquatic environment)

R60

R61

R62

R63

R64

R68

(may impair fertility)

(may cause harm to the unborn child)

(possible risk of impaired fertility)

(possible risk of harm to the unborn child)

(may cause harm to breastfed babies)

(possible risks of irreversible effects)

as laid down in Directive 67/548/EEC and its subsequent amendments, or in Directive 1999/45/EC of the European
Parliament and of the Council of 31 May 1999 concerning the approximation of the laws, regulations and
administrative provisions of the Member States relating to the classification, packaging and labelling of dangerous
preparations (1), and its subsequent amendments.

Each ingredient of any preparation used in the formulation that exceeds 0,01 % by weight of the final product shall
also meet this requirement.

Assessment and verification: The exact formulation of the product shall be provided to the competent body, together
with copies of the material safety data sheets of each ingredient and a declaration of compliance with this criterion.
Test results or references to published data shall be given.

(b) No preservatives shall be used that are or may be classified as R50-53, as laid down in Council Directive 67/548/EEC
and its subsequent amendments or Directive 1999/45/EC and its subsequent amendments, whatever their amount.

Assessment and verification: The exact formulation of the product shall be provided to the competent body, together
with copies of the material safety data for such ingredients (whether substances or preparations) and a declaration of
compliance with this criterion. Test results or references to published data shall be given.

(1) OJ L 200, 30.7.1999, p. 1.

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(c) APEOs, APDs, EDTA, NTA

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:

— alkylphenolethoxylates (APEOs) or other alkyl phenol derivatives (APDs).

— EDTA (ethylene-diamine-tetra-acetate)

— NTA (nitrilotriacetate)

Assessment and verification: The exact formulation of the product shall be provided to the competent body, together
with a declaration of the absence of these chemical compounds.

(d) Phosphonates

The quantity of phosphonates that are not readily biodegradable (aerobically) shall not exceed 0,2 g/wash.

Assessment and verification: The exact formulation of the product shall be provided to the competent body, together
with a declaration of compliance with this criterion.

(a) Nitromusks and polycyclic musks.

4. Fragrances

Nitromusks and polycyclic musks shall not be included in the product, either as part of the formulation or as part of
any preparation included in the formulation. This concerns, amongst others, the following:
musk xylene:
musk ambrette:
moskene:
musk tibetine:
musk ketone:
HHCB:
AHTN:

5-tert-butyl-2,4,6-trinitro-m-xylene
4-tert-butyl-3-methoxy-2,6-dinitrotoluene
1,1,3,3,5-pentamethyl-4,6-dinitroindan
1-tert-butyl-3,4,5-trimethyl-2,6-dinitrobenzene
4(cid:3)-tert-butyl-2(cid:3),6(cid:3)-dimethyl-3(cid:3),5(cid:3)-dinitroacetaphenone
1,3,4,6,7,8-Hexahydro-4,6,6,7,8,8-hexamethylcyclopenta(g)-2-benzopyran
6-Acetyl-1,1,2,4,4,7-hexamethyltetralin

(b) Code of practice

Any ingredients added to the product as a fragrance shall have been manufactured and/or handled following the code
of practice of the International Fragrance Association.

Assessment and verification: The exact formulation of the product shall be provided to the competent body, together
with a declaration of compliance for each part (a) and (b) of this criterion.

5. Packaging

(a) Primary packaging shall not exceed 2,5 grams per functional unit.
(b) Cardboard primary packaging shall consist of ≥ 80 % recycled material.

(c) Plastic primary packaging shall be labelled according to ISO 1043.

Assessment and verification: The applicant shall supply the competent body assessing the application with a sample of the
packaging. A calculation of the quantity of primary packaging and a declaration regarding the percentage of recycled
material

in cardboard packaging shall be submitted to the competent body.

6. Washing performance

The product shall have a satisfactory washing performance at the recommended dosage according to the standard test
developed by IKW or the EN 50242 (modified as below).

The tests shall be carried out at 55 °C or at a lower temperature.

Assessment and verification: The test report shall be submitted to the competent body. A test other than the IKW test or the
modified version of EN 50242 may be used if the competent body assessing the application accepts its equivalence.

If EN 50242: 1998 is used, the following modifications shall apply: the tests shall be carried out at 55 °C ± 2 °C with cold
pre-wash without detergent; the machine used in the test shall be connected to cold water and must hold 12 place
settings with a washing index of between 3,35 and 3,75; the machine's drying programme shall be used, but only the
cleanliness of the dishes shall be assessed; a weak acidic rinsing agent in accordance with the standard (formula III) shall
be used; the rinsing agent setting shall be between 2 and 3; the dosage of dishwashing detergent shall be as recommended
by the manufacturer; three attempts shall be carried out at a water hardness in accordance with the standard; an attempt
consists of five washes where the result is read after the fifth wash without the dishes being cleaned between the washes;
the result shall be better than or identical to the reference detergent after the fifth wash; recipe for the reference detergent
(Detergent B IEC 436) and rinsing agent (formula III), see Appendix B in the standard EN 50242: 1998 (the tensides are to
be stored in a cool place in watertight containers not exceeding 1 kg and are to be used within three months).

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The enzyme production micro-organism shall be absent from the final enzyme preparation.

Assessment and verification: A test report or certificate from the enzyme producer shall be provided to the competent body.

7. Purity of enzymes

8. Consumer information

(a)

Information on the packaging

The following text (or equivalent) shall appear on or in the product:

‘This eco-labelled detergent works well at low temperatures (***). Select low temperature washing cycles on the
dishwasher, wash full loads and do not exceed the recommended dosage. This will minimise both energy and
water consumption and reduce water pollution.

For more information about the Flower:

http://europa.eu.int/ecolabel.

(***) The applicant shall
exceed 55 °C.’

(b) Dosage instructions

insert here the recommended temperature or range of temperatures that shall not

Dosage instructions shall appear on the product packages. The recommended dosages shall be specified for
‘normally’ and ‘heavily’ soiled dishes, and for the ranges of water hardness appropriate to where the product is
marketed. The instructions shall specify how to make best use of the product according to the soil.

The applicant shall take suitable steps to help the consumer respect the recommended dosage, for example by
making available a dosage device (for powdered or liquid products), and/or by indicating the recommended
dosage at least in ml (for powdered or liquid products). A recommendation shall appear on the packaging for
the consumers to contact their water supplier or local authority in order to find out the degree of hardness of
their tap water.

(c)

Information and labelling of ingredients

Commission Recommendation 89/542/EEC of 13 September 1989 concerning the labelling of detergents and
cleaning agents (1) shall be applied and the following groups of ingredients shall be labelled:
Enzymes:
Preservation agents:

indication of the type of enzymes
characterisation and labelling according to IUPAC (International Union of Pure and
Applied Chemistry) nomenclature.

If the product contains perfume,

it shall be indicated on the packaging.

Assessment and verification: The applicant shall provide a sample of the product packaging together with a declara-
tion of compliance with each part (a), (b) and (c) of this criterion.

9. Information appearing on the eco-label

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

‘— helps reduce water pollution,

— helps reduce packaging.’

Assessment and verification: The applicant shall provide the competent body assessing the application with a sample of
the product packaging showing the label, together with a declaration of compliance with this criterion.

(1) OJ L 291, 10.10.1989, p. 55.

Appendix I.A

DID-LIST

DETERGENTS INGREDIENTS DATABASE AND APPROACH TO BE FOLLOWED FOR INGREDIENTS NOT LISTED IN
THE DATABASE

A. The data given below on the most commonly used detergent ingredients shall be used for the calculation of

the ecological criteria

Note: the parameters a NBO, SI, II, THOD as well as the CF-factors for an NBO are not used within this product

group)

Detergent ingredients database (DID-list; version 29. September 1998

DID No

Ingredients

Toxicity

NOEC measured

LTE

Loading factor
(LF)

Anaerobic Non-
Biodegradable (an
NBO)

Aerobic Non-
Biodegradable (a
NBO)

Soluble
inorganics
(SI)

Insoluble
inorganics
(II)

THOD

Anionic surfactants
C 10-13 LAS (Na ø 11,5-11,8, C14<1 %)
other LAS (C14 > 1 %)

C 14/17 Alk. sulfonate

C 8/10 Alkylsulfate

C 12-15 AS

C 12-18 AS

C 16-18 FAS

C 12-15 A 1-3 EO sulphate

C 16/18 A 3-4 EO sulphate

C 8-Dialkylsulfosuccinate

C 12/14 sulpho-fat.-acid methylester

C 16/18 sulpho-fat.-acid methylester

C 14/16 alpha olefine sulphonate

C 14/18 alpha olefine sulphonate

SOAPS C12-22

Nonionic surfactants
C 9/11 A > 3-6 EO lin. or mono br.
C 9/11 A > 6-9 EO lin. or mono br.

C 12/15 A 2-6 EO lin. or mono br.

1

2

3

4

5

6

7

8

9

10

11

12

13

14

15

16

17

18

0,3

0,12

0,27

EC50 = 2,9

0,1

LC50 = 3

0,55

0,15

no valid data

LC50 = 7,5

EC50 = 5

0,15

LC50 = 2,5

LC50 = 1,4

EC0 = 1,6

EC50 = 3,3

EC50 = 5,4

0,18

0,3

0,12

0,27

0,15

0,1

0,15

0,55

0,15

0,1

0,4

0,25

0,15

0,13

0,07

1,6

0,7

1,1

0,18

0,05

0,05

0,03

0,02

0,02

0,02

0,02

0,03

0,03

0,5

0,05

0,05

0,05

0,05

0,05

0,03

0,03

0,03

Y, CF = 0,75

Y, CF = 1,5

Y, CF = 0,75

O

O

O

O

O

O

Y, CF = 1,5

Y, CF = 0,75

Y, CF = 0,75

Y, CF = 0,75

Y, CF = 2,0

O

O

O

O

O

O

O

O

O

O

O

O

O

O

O

O

O

O

O

O

O

O

O

O

O

O

O

O

O

O

O

O

O

O

O

O

O

O

O

O

O

O

O

O

O

O

O

O

O

O

O

O

O

O

O

O

O

O

2,3

2,3

2,5

1,9

2,2

2,3

2,5

2,1

2,2

2

2,1

2,3

2,3

2,4

2,9

2,4

2,2

2,5

.

.

1
5
1
2
0
0
3

E
N

O

f
f
i
c
i
a
l

J
o
u
r
n
a
l

o
f

t
h
e

E
u
r
o
p
e
a
n
C
o
m
m
u
n
i
t
i
e
s

L

9
/
1
9

DID No

Ingredients

Toxicity

NOEC measured

LTE

Loading factor
(LF)

Anaerobic Non-
Biodegradable (an
NBO)

Aerobic Non-
Biodegradable (a
NBO)

Soluble
inorganics
(SI)

Insoluble
inorganics
(II)

THOD

19

20

21

22

23

24

25

26

27

28

29

30

31

32

33

34

35

36

C 12-15 (Avg. C < 14) A > 6-9 EO lin. or mono br.
C 12-15 (Avg. C > 14) A > 6-9 EO
C 12-15 A > 9-12 EO
C 12-15 A > 20-30 EO
C 12-15 A > 30 EO

C 12/18 A 0-3 EO

C 12-18 A 9 EO

C 16/18 A 2-6 EO
C 16/18 A > 9-12 EO

C 16/18 A 20-30 EO
C 16/18 A > 30 EO

C 12/14 Glucose amide

C 16/18 Glucose amide

C 12/14 Alkylpolyglucoside

Amphoteric surfactants

C 12-15 Alkyl dimethylbetaine

C 12-18 Alkyl amidopropylbetaine

Sud controllers

Silicone

Paraffin

Fabric softening

0,24

0,17

LC50 = 0,8

EC50 = 13

LC50 = 130

no data

0,2

0,03

LC50 = 0,5

EC50 = 18

LC50 = 50

4,3

0,116

1

0,03

0,03

EC50 = 241

no data

0,24

0,17

0,3

0,65

6,5

0,01

0,2

0,03

0,05

0,36

2,5

4,3

0,116

1

0,03

0,03

4,82

100

37

Glycerol

Builders

LC50 > 5-10 gl

1 000

38

39

40

41

42

43

Phosphate as sodium-tri-polyphosphate (STPP)

Zeolite A

Citrate

Polycarboxylates and related derivates

Clay

120

EC50 = 85

124

Carbonate /bicarbonate

LC50 = 250

1 000

120

85

124

1 000

250

0,03

0,03

0,03

0,05

0,75

0,03

0,03

0,03

0,03

0,05

0,75

0,03

0,03

0,03

0,05

0,05

0,4

0,4

0,13

0,6

0,05

0,07

0,4

0,05

0,8

O

O

O

O

O

O

O

O

O

O

O

O

O

O

Y, CF = 2,5

Y, CF = 2,5

Y, CF = 0,75

O

O

O

O

O

Y, CF = 0,1

O

O

O

O

O

O

Y

O

O

O

O

O

Y

O

O

O

O

O

Y

Y

O

O

O

O

Y

O

O

O

O

O

O

O

O

O

O

O

O

O

O

O

O

O

O

O

O

O

Y

O

O

O

O

Y

O

O

O

O

O

O

O

O

O

O

O

O

O

O

O

O

O

O

O

O

Y

O

O

Y

O

2,3

2,3

2,2

2

0 (*)

2,9

2,4

2,6

2,3

2,1

0 (*)

2,2

2,5

2,3

2,9

2,8

0,0

0 (*)

1,2

0,0

0,0

0,6

0 (*)

0,0

0,0

L

9
/
2
0

E
N

O

f
f
i
c
i
a
l

J
o
u
r
n
a
l

o
f

t
h
e

E
u
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o
p
e
a
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C
o
m
m
u
n
i
t
i
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s

.

.

1
5
1
2
0
0
3

DID No

Ingredients

44

45

46

47

48

49

50

51

52

53

54

55

56

57

58

59

60

61

62

63

64

65

66

67

68

69

Fatty acid (C ≥ 14)

Silicate / disilicate

NTA

Polyaspartic acid. Na salt

Bleaching

Perborate mono (as borate)

Perborate tetra (as borate)

Percarbonate (see carbonate)

TAED

Solvents

C 1 - C 4 alcohols

Monoethanolamine

Diethanolamine

Triethanolamine

Miscellaneous

Polyvinylpyrrolidon (PVP / PVNO / PVPVI)

Phosphonates

EDTA

CMC

Na Sulphate

Mg Sulphate

Na Chloride

Urea

Maleic acid

Malic acid

Ca formiate

Silica
High MW polymers PEG > 4000
Low MW polymers PEG > 4000

Toxicity

NOEC measured

EC0 = 1,6
EC50 > 1 000

19

125

1 - 10

1 - 10

LTE

1,6

1 000

19

12,5

6

6

LC50 = 250

250

EC0 = 500

EC0 = 500

LC50 = 8 000

0,78

0,78

0,78

EC50 > 100

7,4

LOEC = 11
LC50 > 250

EC50 = 2 460

EC50 = 788

EC50 = 650
LC50 > 10 000

LC50 = 106

LC50 = 106

100

0,78

0,78

0,78

100

7

11

250

1 000

800

650

100

2,1

2,1

100

100

100

100

Loading factor
(LF)

Anaerobic Non-
Biodegradable (an
NBO)

Aerobic Non-
Biodegradable (a
NBO)

Soluble
inorganics
(SI)

Insoluble
inorganics
(II)

THOD

.

.

1
5
1
2
0
0
3

0,05

0,8

0,13

0,13

1

1

0,8

0,13

0,13

0,13

0,13

0,13

0,75

0,4

1

0,75

1

1

1

0,13

0,13

0,13

0,13

0,05

0,4

0,13

O

O

O

Y, CF = 0,1

O

O

O

O

O

O

O

O

Y, CF = 0,1

Y, CF = 0,5

Y, CF = 0,1

Y, CF = 0,1

O

O

O

O

O

O

O

O

O

O

O

O

O

O

O

O

O

O

O

O

O

O

Y

Y

Y

Y

O

O

O

O

O

O

O

O

Y

O

O

Y

O

O

Y

Y

Y

O

O

O

O

O

O

O

O

O

Y

Y

Y

O

O

O

O

O

O

O

O

O

O

O

O

O

O

O

O

O

O

O

O

O

O

O

O

O

O

O

O

O

O

Y

O

O

2,9

0,0

0,6

1,2

0,0

0,0

0,0

2,0

2,3

2,4

2,3

2

0 (*)

0 (*)

0 (*)

0 (*)

0,0

0,0

0,0

2,1

0,8

0,6

2,0

0,0

0 (*)

1,1

E
N

O

f
f
i
c
i
a
l

J
o
u
r
n
a
l

o
f

t
h
e

E
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DID No

Ingredients

Toxicity

70

71

72

73

74

75

76

77

78

79

80

81

82

83

84

85

Cumene sulfonate

Xylene sulfonate

Toluene sulfonates

Na-/Mg-/KOH

Enzymes

Perfume formulation as used

Dyes

Starch

Zn phthalocyanine sulfonate

Anionic polyester (Soil release polymer)

Iminodisuccinate

Optical brighteners = FWA

FWA 1 (1)

FWA 5 (2)

Additional

ingredients

Alkyl aminoxides (C12-18)

Glycereth (6-17EO) cocoate

Phosphate esters (C12-18)

NOEC measured

LC50 = 66

LC50 = 66

LC50 = 66

LC50 = 25

LC50 = 2-10

LC50 = 10

no data

0,16

EC50 = 310

23

LC0 = 10

3,13

0,08

EC50 = 32

EC50 = 38

LTE

6,6

6,6

6,6

100

25

0,02

0,1

250

0,016

310

2,3

1,0

3,13

0,08

1,6

1,9

Loading factor
(LF)

Anaerobic Non-
Biodegradable (an
NBO)

Aerobic Non-
Biodegradable (a
NBO)

Soluble
inorganics
(SI)

Insoluble
inorganics
(II)

THOD

0,13

0,13

0,13

1

0,13

0,1

0,4

0,1

0,07 (**)

0,4

0,13

0,4

0,4

0,05

0,05

0,05

Y, CF = 0,25

Y, CF = 0,25

Y, CF = 0,25

O

O

Y, CF = 3,0

Y, CF = 3,0

O

Y, CF = 2,5

Y, CF = 0,1

Y, CF = 2,5

Y, CF = 1,5

Y, CF = 0,5

Y, CF = 2,5

O

Y, CF = 2,5

O

O

O

O

O

Y

Y

O

Y

Y

O

Y

Y

O

O

O

O

O

O

Y

O

O

O

O

O

O

O

O

O

O

O

O

O

O

O

O

O

O

O

O

O

O

O

O

O

O

O

O

1,7

1,6

1,4

0,0

2,0

0 (*)

0 (*)

0,97

0 (*)

0 (*)

1,1

0 (*)

0 (*)

3,2

2,1

2,3

FWA 1 = Disodium 4.4-bis (4-anilino-5-morpholino-1,3,5-triazin-2-yl)amino stilbene-2.2-disulfonate
FWA 5 = Disodium 4.4-bis(2-sulfostryryl)biphenyl

(1)
(2)
(*) THOD for aerobically non degradable organic substances is set to zero
(**) rapid photodegradation

Notes:
Y
O
LTE

= yes, criterion applies
= no, criterion does not apply
= long term effect concentration

NOEC = non observed effect concentration
CF
THOD = theoretical oxygen demand

= correction factor for anaerobic non degradable organic substances

L

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E
N

O

f
f
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J
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a
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t
h
e

E
u
r
o
p
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a
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C
o
m
m
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s

.

.

1
5
1
2
0
0
3

15.1.2003

EN

Official Journal of the European Communities

L 9/23

The following approach applies, as appropriate in the case of ingredients that are not listed on the DID-list

Appendix I.B

Aquatic toxicity

The lowest validated long-term effect (LTE) data on fish, daphnia magna or algae should be considered for the calculation
of the critical dilution volume criterion (toxicity).

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.

In the absence of LTE data the following procedure has to be applied in order to estimate the LTE data by using the
specified uncertainty factor (UF) on the data of the most sensitive species:

Non surfactants

DATA AVAILABLE

UF TO BE USED

At least 2 acute LC50 on fish or daphnia or algae
1 NOEC on fish or daphnia or algae

2 NOEC on fish or daphnia or algae

3 NOEC on fish, daphnia or algae

100

10

5

1

Take lowest validated NOEC

Deviation from this rule may be admitted if evidence can be provided that lower factors or data can be scientifically
justified. NOEC is the No Observed Effect Concentration (in a chronic test).

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 (NOEC-if species is most sensitive in acute toxicity)

3 LC50 on fish or daphnia or algae
At least 1 LC50 on fish, daphnia or algae

10 (NOEC-if species is not the most sensitive in acute
toxicity)

20 (lowest LC50)
50 (lowest LC50)
or 20 in specific cases (see below)

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 or algal 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 should be 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 if such QSARs can be established.

Any deviation from the above-described scheme has to be well reasoned for the specific chemical.

Loading factors

Loading factors shall be established according to Commission Directive 93/67/EEC of 20 July 1993 laying down the
principles for assessment of risk to man and the environment of substances (1) notified in accordance with Council
Directive 67/548/EEC and to Council Regulation (EEC) No 793/93 (2).

(1) OJ L 227, 8.9.1993, p. 9.
(2) OJ L 84, 5.4.1993, p. 1.

L 9/24

EN

Official Journal of the European Communities

15.1.2003

Non-biodegradable organics (anaerobic): flow diagram to define correction factors (CF) (1)

(1) The correction factors are to be established on the basis of the ingredient properties and applied to the dosage expressed in g/wash.

15.1.2003

EN

Official Journal of the European Communities

L 9/25

Appendix I.C

Doc u me nta ti on of a na e r ob i c bi ode g ra da bi li ty

The following approach may be used to provide the necessary documentation of anaerobic degradability in the case of
ingredients that are not listed in the DID-list:

1. Apply reasonable extrapolation

Use test results obtained with one raw material to extrapolate the ultimate anaerobic degradability of structurally
related surfactants. If anaerobic biodegradability has been confirmed for a surfactant (or a group of homologues)
according to the DID-list, it can be assumed that a similar type of surfactant is also anaerobically biodegradable (e.g.,
C12-15 A 1-3 EO sulphate (DID No 8) is anaerobically biodegradable, and a similar anaerobic biodegradability may
also be assumed for C12-15 A 6 EO sulphate). If anaerobic biodegradability has been confirmed for a surfactant by
use of an appropriate test method, it can be assumed that a similar type of surfactant is also anaerobically biodegrad-
able (e.g., literature data confirming the anaerobic biodegradability of surfactants belonging to the group alkyl ester
ammonium salts may be used as documentation for a similar anaerobic biodegradability of other quaternary ammo-
nium salts containing ester-linkages in the alkyl chain(s)).

2. Perform screening test for anaerobic degradability

If new testing is necessary, perform a screening test by use of ISO 11734, ECETOC No 28 (June 1988) or an equiva-
lent method.

3. Perform low-dosage degradability test

If new testing is necessary, and in the case of experimental problems in the screening test (e.g. inhibition due to toxi-
city of test substance), repeat testing by using a low dosage of surfactant and monitor degradation by 14C measure-
ments or chemical analyses. Testing at low dosages may be performed by use of OECD 308 (August 2000) or an
equivalent method.