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Reaction mass of Tetrasodium 2-[{4-[{4-[(4-amino-6-chloro-1,3,5-triazin-2-yl)amino]-5-sulfonatonaphthalen-1-yl}diazenyl]-7-sulfonatonaphthalen-1-yl}diazenyl]benzene-1,4-disulfonate and Tetrasodium 2-[{4-[{4-[(4-amino-6-chloro-1,3,5-triazin-2-yl)amino]-5-sulfonatonaphthalen-1-yl}diazenyl]-6-sulfonatonaphthalen-1-yl}diazenyl]benzene-1,4-disulfonate
EC number: 916-837-8 | 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: inherent biodegradability
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Study period:
- 1987
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- study well documented, meets generally accepted scientific principles, acceptable for assessment
- Justification for type of information:
- None
- Qualifier:
- according to guideline
- Guideline:
- other: CIBA Method A-37
- Qualifier:
- equivalent or similar to guideline
- Guideline:
- OECD Guideline 302 B (Inherent biodegradability: Zahn-Wellens/EMPA Test)
- Principles of method if other than guideline:
- None
- GLP compliance:
- no
- Specific details on test material used for the study:
- None
- Oxygen conditions:
- aerobic
- Inoculum or test system:
- activated sludge (adaptation not specified)
- Details on inoculum:
- Activated sludge should be taken from a municipal waste water treatment plant which has been rinsed with municipal water for 2 times. The sediment is taken to estimate the dry weight according to method A-26. The activated sludge is prepared one day before the start of the experiment, ventilated overnight and adjusted to a concentration of 600 mg/L.
- Duration of test (contact time):
- 28 d
- Details on study design:
- None
- Preliminary study:
- None
- Test performance:
- None
- Key result
- Parameter:
- % degradation (DOC removal)
- Value:
- 8
- Remarks on result:
- other: not inherently biodegradable
- Details on results:
- None
- Results with reference substance:
- None
- Validity criteria fulfilled:
- yes
- Interpretation of results:
- under test conditions no biodegradation observed
- Conclusions:
- Biodegradation of the test substance after 28 days was 8 %.
- Executive summary:
The inherent biodegradability of FAT 40034/D was determined in a Zahn-Wellens test. The bio-elimination of FAT 40032/D was found to be 8 % (DOC).
- Endpoint:
- biodegradation in water: ready biodegradability
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Study period:
- 1987
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- study well documented, meets generally accepted scientific principles, acceptable for assessment
- Qualifier:
- according to guideline
- Guideline:
- other: CIBA Method A-15
- Principles of method if other than guideline:
- None
- GLP compliance:
- no
- Specific details on test material used for the study:
- None
- Oxygen conditions:
- aerobic
- Inoculum or test system:
- activated sludge (adaptation not specified)
- Details on inoculum:
- None
- Duration of test (contact time):
- 5 d
- Details on study design:
- None
- Preliminary study:
- None
- Test performance:
- None
- Remarks on result:
- other: BOD5 tested
- Details on results:
- None
- Key result
- Parameter:
- BOD5
- Value:
- 13 mg O2/g test mat.
- Results with reference substance:
- None
- Validity criteria fulfilled:
- yes
- Interpretation of results:
- under test conditions no biodegradation observed
- Conclusions:
- The BOD of FAT 40032/D is: 13 mg O2/g test mat.
- Executive summary:
The biochemical oxygen demand of FAT 40032/D 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 that contains a seed of microorganisms. The test was carried out according to CIBA Method A-15. The BOD5 of FAT 40032/D is 13 mg O2/g test material.
- Endpoint:
- biodegradation in water: ready biodegradability
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Study period:
- 1987
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- study well documented, meets generally accepted scientific principles, acceptable for assessment
- Justification for type of information:
- None
- Qualifier:
- according to guideline
- Guideline:
- other: CIBA Method A-22
- Principles of method if other than guideline:
- None
- GLP compliance:
- no
- Specific details on test material used for the study:
- None
- Oxygen conditions:
- aerobic
- Inoculum or test system:
- activated sludge (adaptation not specified)
- Details on inoculum:
- None
- Duration of test (contact time):
- 5 d
- Details on study design:
- None
- Preliminary study:
- None
- Test performance:
- None
- Remarks on result:
- other: COD was determined
- Details on results:
- None
- Key result
- Parameter:
- COD
- Value:
- 935 mg O2/g test mat.
- Results with reference substance:
- None
- Validity criteria fulfilled:
- yes
- Interpretation of results:
- under test conditions no biodegradation observed
- Conclusions:
- The COD of the test substance FAT 40032/D is: 935 mg O2/g.
- Executive summary:
A study was performed to determine the chemical oxygen demand of FAT 40032/D according CIBA Method A-22. The COD of FAT 40032/D is 935 mg O2/g
Referenceopen allclose all
None
None
None
Description of key information
FAT 40032 is not readily biodegradable.
Key value for chemical safety assessment
- Biodegradation in water:
- under test conditions no biodegradation observed
Additional information
The key study was performed to determine the percent biodegradation of FAT 40032/D. The biological elimination of FAT 40032/D is found to be 8 %. The chemical oxygen demand of FAT 40032/D was found to be 935 mg O2/g test material whereas the biological oxygen demand was found to be 13 mg O2/g test material. Therefore, the corresponding BOD5/COD quotient is 0.014 indicating the substance to be not biodegradable. Several other studies showed the following results:
COD of 906.3 mg O2/g test material.
BOD5 of 0 mg O2/g test material.
COD of 247.41 mg O2/g test material.
COD of 649.74 mg O2/g test material.
For all tests, the relevant BOD5/COD quotient is <0.5, therefore the substance is not indicative of rapid degradation. Considering the data from key study and supporting studies, the test substance FAT 40032 is not biodegradable.
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