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Reaction mass of Trisodium 4-({4-chloro-6-[(4-sulfonatophenyl)amino]-1,3,5-triazin-2-yl}amino)-2-{[1-ethyl-2-hydroxy-4-methyl-6-oxo-5-(sulfonatomethyl)-1,6-dihydropyridin-3-yl]diazenyl}benzenesulfonate and Trisodium 4-({4-chloro-6-[(3-sulfonatophenyl)amino]-1,3,5-triazin-2-yl}amino)-2-{[1-ethyl-2-hydroxy-4-methyl-6-oxo-5-(sulfonatomethyl)-1,6-dihydropyridin-3-yl]diazenyl}benzenesulfonate
EC number: 944-218-2 | CAS number: -
- Life Cycle description
- Uses advised against
- Endpoint summary
- Appearance / physical state / colour
- Melting point / freezing point
- Boiling point
- Density
- Particle size distribution (Granulometry)
- Vapour pressure
- Partition coefficient
- Water solubility
- Solubility in organic solvents / fat solubility
- Surface tension
- Flash point
- Auto flammability
- Flammability
- Explosiveness
- Oxidising properties
- Oxidation reduction potential
- Stability in organic solvents and identity of relevant degradation products
- Storage stability and reactivity towards container material
- Stability: thermal, sunlight, metals
- pH
- Dissociation constant
- Viscosity
- Additional physico-chemical information
- Additional physico-chemical properties of nanomaterials
- Nanomaterial agglomeration / aggregation
- Nanomaterial crystalline phase
- Nanomaterial crystallite and grain size
- Nanomaterial aspect ratio / shape
- Nanomaterial specific surface area
- Nanomaterial Zeta potential
- Nanomaterial surface chemistry
- Nanomaterial dustiness
- Nanomaterial porosity
- Nanomaterial pour density
- Nanomaterial photocatalytic activity
- Nanomaterial radical formation potential
- Nanomaterial catalytic activity
- Endpoint summary
- Stability
- Biodegradation
- Bioaccumulation
- Transport and distribution
- Environmental data
- Additional information on environmental fate and behaviour
- Ecotoxicological Summary
- Aquatic toxicity
- Endpoint summary
- Short-term toxicity to fish
- Long-term toxicity to fish
- Short-term toxicity to aquatic invertebrates
- Long-term toxicity to aquatic invertebrates
- Toxicity to aquatic algae and cyanobacteria
- Toxicity to aquatic plants other than algae
- Toxicity to microorganisms
- Endocrine disrupter testing in aquatic vertebrates – in vivo
- Toxicity to other aquatic organisms
- Sediment toxicity
- Terrestrial toxicity
- Biological effects monitoring
- Biotransformation and kinetics
- Additional ecotoxological information
- Toxicological Summary
- Toxicokinetics, metabolism and distribution
- Acute Toxicity
- Irritation / corrosion
- Sensitisation
- Repeated dose toxicity
- Genetic toxicity
- Carcinogenicity
- Toxicity to reproduction
- Specific investigations
- Exposure related observations in humans
- Toxic effects on livestock and pets
- Additional toxicological data
Biodegradation in water: screening tests
Administrative data
Link to relevant study record(s)
- Endpoint:
- biodegradation in water: ready biodegradability
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Study period:
- Study initiation date - 05 November 1992; Experiment start date - 11 November 1992; Experiment completion date - 17 November 1992; Study completion date - 17 December 1992
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- guideline study
- Qualifier:
- according to guideline
- Guideline:
- ISO 5815 (Water quality - Determination of Biochemical Oxygen Demand after 5 Days (BOD5) - Dilution and Seeding Method)
- Deviations:
- no
- GLP compliance:
- yes (incl. QA statement)
- Specific details on test material used for the study:
- Code number: FAT 40000/G
Batch number: 67/92
Purity: 79.5%
Appearance: solid
Solubility: miscible
Storage: room temperature
Expiration date: 01 June 1993. - Oxygen conditions:
- aerobic
- Inoculum or test system:
- sewage, predominantly domestic (adaptation not specified)
- Details on inoculum:
- Seeding water of an urban waste water
- Duration of test (contact time):
- 5 d
- Initial conc.:
- >= 6.6 - <= 844.6 mg/L
- Based on:
- test mat.
- Parameter followed for biodegradation estimation:
- O2 consumption
- Details on study design:
- Validity
Blank: BOD5 : should preferably not exceed 0.5 mg O2/I
Reference substance: BOD5 : between 180 - 230 mg O2/I
Test substance: O2-concentration after 5 days : between one-third and two-thirds of the initial O2-concentration. - Reference substance:
- other: D(+) - Glucose/L-Glutamic acid
- Remarks on result:
- not measured/tested
- Key result
- Parameter:
- BOD5
- Value:
- 3 mg O2/g test mat.
- Results with reference substance:
- The BOD5 of the reference substance is: 195,180, 200 mg O2/I.
- Validity criteria fulfilled:
- yes
- Interpretation of results:
- under test conditions no biodegradation observed
- Conclusions:
- The BOD of test item was found to be 3.0 mg O2/g test mat.
- Executive summary:
The biochemical oxygen demand of test item was determined by measuring the dissolved oxygen concentration before and after 5 days incubation at 20°C in different test concentrations diluted in water saturated with dissolved oxygen and containing a seed of microorganisms. This study was conducted according to ISO 5815 Second Edition 1989-08-01 (E) in a GLP certified laboratory.
The test substance was tested in concentrations from about 6 to 800 mg/l. The reference substance D(+)-Glucose / L-Glutamic acid was tested in a concentration of 20 mg/l.
Based on the findings of this study, the BOD5 of test item was found to be 3 mg 02/g. In another study, the COD of same test item was determined to be 402 mgO2/g. The resultant BOD COD ratio was found to be 0.007 indicating the substance is not readily biodegradable.
The BOD5 of the reference substance is: 195,180, 200 mg O2/I
- Endpoint:
- biodegradation in water: ready biodegradability
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Study period:
- Study initiation date - 21 October 1992; Experiment start date - 26 October 1992; Experiment completion date - 27 October 1992; Study completion date - 23 November 1992.
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- guideline study
- Qualifier:
- according to guideline
- Guideline:
- other: EEC Directive 84/449 (1984), Part. C.9 according to DEV H 41-1, Deutsches Einheits-Verfahren, 1980
- Deviations:
- yes
- Remarks:
- Mean of 2 determinations instead of 3
- GLP compliance:
- yes (incl. QA statement)
- Specific details on test material used for the study:
- Code number: FAT 40000/G
Batch number: 67/92
Purity: 79.5%
Appearance: solid
Solubility: miscible
Storage: room temperature
Expiration date: 01 June 1993. - Oxygen conditions:
- aerobic
- Inoculum or test system:
- other: Titration method
- Duration of test (contact time):
- 2 h
- Initial conc.:
- 5 mg/L
- Based on:
- COD
- Parameter followed for biodegradation estimation:
- O2 consumption
- Reference substance:
- other: Potassium hydrogen phthalate solution
- Remarks on result:
- not measured/tested
- Key result
- Parameter:
- COD
- Value:
- 402 mg O2/g test mat.
- Results with reference substance:
- The COD of the reference substance is: 193 mg O2/I
- Validity criteria fulfilled:
- yes
- Interpretation of results:
- under test conditions no biodegradation observed
- Conclusions:
- The COD of the test substance was found to be 402 mg O2/g.
- Executive summary:
The COD of test item was determined to calculate the BOD:COD ratio as a measure of ready biodegradation. A pre-determinated amount of the test substance dissolved in water is oxidized by potassium dichromate in a strong sulphuric acid medium with silver sulphate as a catalyst under reflux for 2 hours. The residual dichromate is determined by titration with standardized ferrous ammonium sulphate (according to DEV H 41-1, DEV1980).
The test substance concentration was tested in 5.0 mg/l. The reference substance Potassium hydrogen phthalate solution was tested in a concentration of 20 ml/I. The COD of test item was found to be 402 mg O2/g. The BOD of same test substance was determined to be 3 mgO2/g in another study. The resultant BOD:COD ratio was calculated to be 0.007, indicating the substance to be not readily biodegradable. The COD of the reference substance is: 193 mg O2/I
- Endpoint:
- biodegradation in water: inherent biodegradability
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Study period:
- Study initiation date - 04 February 1993; Experiment start date - 17 February 1993; Experiment completion date - 17 March 1993; Study completion date - 07 April 1993
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- guideline study
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 302 B (Inherent biodegradability: Zahn-Wellens/EMPA Test)
- Deviations:
- no
- GLP compliance:
- yes (incl. QA statement)
- Specific details on test material used for the study:
- Code number: FAT 40000/G
Batch number: 67/92
Purity: 79.5%
Appearance: solid
Solubility: miscible
Storage: room temperature
Expiration date: 01 June 1993. - Oxygen conditions:
- aerobic
- Inoculum or test system:
- sewage, domestic (adaptation not specified)
- Details on inoculum:
- Sludge of a biological sewage treatment plant (ARA-Basel Industries) collected on 16.02.93
- Duration of test (contact time):
- 28 d
- Initial conc.:
- 150 mg/L
- Based on:
- DOC
- Parameter followed for biodegradation estimation:
- O2 consumption
- Reference substance:
- diethylene glycol
- Key result
- Parameter:
- % degradation (DOC removal)
- Value:
- 0
- Sampling time:
- 28 d
- Remarks on result:
- other: Standard deviation not available
- Details on results:
- Test substance
The bioelimination of FAT - 40'000/G measured as DOC after 28 days corrected by the blank control is: 0 % (average of 2 tests running in parallel)
Adsorption after 3 hours: 2.5 %
Reference substance: The bioelimination, corrected by the blank control and measured as DOC (mg/l) is: 95.2 % 16th day - Results with reference substance:
- The bioelimination of the reference substance after 16 days is : 95.2 %.
- Validity criteria fulfilled:
- yes
- Interpretation of results:
- under test conditions no biodegradation observed
- Conclusions:
- Biodegradation of the test substance after 28 days was 0 %.
- Executive summary:
A key study was performed to determine the percent biodegradation of the test item. This study was conducted according to OECD test guideline 302B in a GLP certified laboratory.
The test substance was tested in a concentration of 150 mg/l. The reference substance was diethylene glycol.
Based on the results of the study, biodegradation of the test substance after 28 days was 0 %. The test item is not inherently biodegradable.
Referenceopen allclose all
|
Reference |
Substance |
|||||
Zeit |
Datum |
Mean Value of the Reference DOC (mg/l) |
Value of the Blank DOC (mg/l) |
Elimination % |
Mean Value of the Substance DOC (mg/l) |
Value of the Blank DOC (mg/l) |
Elimination % |
-1 day |
16.02.93 |
155.6 |
- |
... |
147.6 |
--- |
... |
0 |
17.02.93 |
165.8 |
7.3 |
0 |
154.2 |
7.3 |
0.5 |
3 h |
17.02.93 |
169.3 |
12.1 |
0 |
156.0 |
12.1 |
2.5 |
2.day |
19.02.93 |
177.6 |
14.3 |
0 |
162.5 |
14.3 |
0 |
5.day |
22.02.93 |
123.8 |
20.1 |
33.4 |
163.3 |
20.1 |
3.0 |
7.day |
24.02.93 |
62.7 |
24.2 |
75.3 |
165.4 |
24.2 |
4.3 |
8.day |
25.02.93 |
28.2 |
24.0 |
97.3 |
-- |
... |
... |
9 day |
26.02.93 |
35.5 |
30.5 |
96.8 |
172.4 |
30.5 |
3.9 |
12 day |
01.03.93 |
31.0 |
22.5 |
94.5 |
172.6 |
22.5 |
0 |
13 day |
02.03.93 |
31.6 |
17.4 |
90.9 |
... |
... |
... |
14 day |
03.03.93 |
31.7 |
18.2 |
91.3 |
170.5 |
18.2 |
0 |
15 day |
04.03.93 |
27.4 |
16.4 |
92.9 |
--- |
... |
... |
16 day |
05.03.93 |
26.6 |
19.2 |
95.2 |
169.9 |
19.2.' |
0 |
19.day |
08.03.93 |
... |
... |
... |
174.3 |
19.4 |
0 |
21.day |
10.03.93 |
... |
--- |
--- |
165.7 |
15.3 |
0 |
23.day |
12.03.93 |
--- |
... |
-- |
169.2 |
15.9 |
0 |
26.day |
15.03.93 |
--- |
... |
--- |
174.0 |
13.3 |
0 |
28 day |
17.03.93 |
--- |
--- |
... |
171.8 |
15.4 |
0 |
Description of key information
The test substance was determined to be not readily nor inherently biodegradable.
Key value for chemical safety assessment
- Biodegradation in water:
- not biodegradable
- Type of water:
- freshwater
Additional information
A key study was performed to determine the percent biodegradation of FAT 40000. An inherent biodegradability of FAT 40000 was determined in a 28 days Test according to the OECD Guideline for Testing of Chemicals, No. 302B. The test substance was tested in a concentration of 150 mg/l. The reference substance was diethylene glycol. Based on the results of the study, biodegradation of the test substance after 28 days was 0 %.
The biochemical oxygen demand of FAT 40000/G is determined by measuring the dissolved oxygen concentration before and after 5 days incubation at 20°C in different test concentrations diluted in water saturated with dissolved oxygen and containing a seed of microorganisms. The test substance was tested in concentrations from about 6 to 800 mg/l. The reference substance D(+)-Glucose / L-Glutamic acid was tested in a concentration of 20 mg/l. The BOD5 of FAT 40000/G: 3 mg 02/g The BOD5 of the reference substance is : 195,180, 200 mg O2/l.
A pre-determinated amount of the test substance FAT 40000/G dissolved in water is oxidized by potassium dichromate in a strong sulphuric acid medium with silver sulphate as a catalyst under reflux for 2 hours. The residual dichromate is determined by titration with standardized ferrous ammonium sulphate (according to DEV H 41-1, DEV1980). The test substance concentration was tested in 5.0 mg/l. The reference substance Potassium hydrogen phthalate solution was tested in a concentration of 20 ml/I. The COD of FAT 40000/G is : 402 mg 02/g The COD of the reference substance is: 193 mg O2/l.
Based on these results the corresponding BOD5/COD quotient is equivalent to zero, so no biodegradation is expected.
Other supporting studies were also performed with following results -
COD:
FAT 40000/E = 771 mg O2/g, FAT 40000/D = 157 mg O2/g, 40000/A = 417 mg O2/g, FAT 40000 = 581 mg O2/g
BOD5 of FAT 40000/E, FAT 40000/D, FAT 40000/A, FAT 40000 were all found to be 0 mg O2/g
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