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EC number: 279-914-9 | CAS number: 82199-12-0
- 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
Hydrolysis
Administrative data
Link to relevant study record(s)
- Endpoint:
- hydrolysis
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Study period:
- From 22 MAR 2004 to 01 APR 2004
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- guideline study
- Remarks:
- according to OECD 111
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 111 (Hydrolysis as a Function of pH)
- Deviations:
- no
- Qualifier:
- according to guideline
- Guideline:
- EU Method C.7 (Degradation: Abiotic Degradation: Hydrolysis as a Function of pH)
- Deviations:
- no
- GLP compliance:
- not specified
- Radiolabelling:
- no
- Analytical monitoring:
- yes
- Details on sampling:
- The samples were taken out of the water bath and cooled down to room temperature to stop the hydrolysis reaction. The samples were filtrated and the pH of the clear solutions was measured. All samples were dissolved 1 mL to 10 mL with acetonitrile and then placed into the GC auto sampler for analysis.
- Buffers:
- - Standard buffer solution pH 4.00, Bernhard Kraft, Art.-No.: 03083.3000, (Citric acid / NaOH / NaCI)
- Standard buffer solution pH 7.00, Riedel-de Haän, Art.-No.: 33546 (KH2PO4 / Na2HPO4) with fungicidal additive
- Standard buffer solution pH 9.00, Riedel-de Haen, Art.-No.: 33548 (Borax / HCI) with fungicidal additive) - Estimation method (if used):
- To quantify the degree of degradation of the test substance, the concentration of the degradation product methanol was determined. The aim of his preliminary test was to determine if the degradation of the test item would be below 10% after 5 days at 50 deg C for all tested pH-values (then no further testing required according to the guideline). Therefore it was assumed that for 10% of hydrolysis from one mole of test substance at minimum 0.1 mole of methanol would have to be formed (see table under "Any other information on materials and methods incl. tables").
- Details on test conditions:
- PREPARATION OF-THE PRELIMINARY TEST SUSPENSIONS
Because of the very low solubility of the test substance in water and due to the fact that no direct quantification of the substance was possible, suspensions of the test substance in the buffer solutions were prepared. Therefore in each case approximately 200 mg of the test substance were mixed with 100 mL of the corresponding buffer solution.
The initial nominal concentrations are given under "Any other information on materials and methods incl. tables".
PERFORMANCE OF THE PRELIMINARY TEST
A sufficient number of vials were filled with each test solution. The vials were closed, packed into small plastic bags to protect them from light, and incubated in a water bath at 50.0°C. According to the sampling schedule below, samples were taken out of the water bath, cooled down to room temperature, filtrated (0.45 µm), diluted 1:10 with acetonitrile and placed in the GC autosampler. All vials were injected twice.
Determination of the degree of degradation: See "Estimation method (if used)" - Duration:
- 217.5 h
- pH:
- 4
- Temp.:
- 50 °C
- Initial conc. measured:
- 2.235 g/L
- Remarks:
- the value represents the nominal concentration (4.93 mmol/L)
- Duration:
- 217.5 h
- pH:
- 7
- Temp.:
- 50 °C
- Initial conc. measured:
- 2.024 g/L
- Remarks:
- the value represents the nominal concentration (4.46 mmol/L)
- Duration:
- 217.5 h
- pH:
- 9
- Temp.:
- 50 °C
- Initial conc. measured:
- 1.849 g/L
- Remarks:
- the value represents the nominal concentration (4.08 mmol/L)
- Number of replicates:
- One
- Positive controls:
- no
- Negative controls:
- no
- Preliminary study:
- All measured methanol concentrations were far below the theoretical concentration of methanol expected to evolve after 10% degradation of the test substance. Therefore the submission substance is considered to be stable at normal environmental conditions. The measured degradation of the test substance at pH 4, 7 and 9 at 50°C corresponds to a half-life time of more than one year under outdoor conditions. Therefore no further testing had to be performed at all pH-values.
- Transformation products:
- no
- Details on hydrolysis and appearance of transformation product(s):
- No hydrolysis observed.
- pH:
- 4
- Temp.:
- 50 °C
- Remarks on result:
- hydrolytically stable based on preliminary test
- pH:
- 7
- Temp.:
- 50 °C
- Remarks on result:
- hydrolytically stable based on preliminary test
- pH:
- 9
- Temp.:
- 50 °C
- Remarks on result:
- hydrolytically stable based on preliminary test
- Details on results:
- As in the preliminary study at 50°C at all three pH-values (4.0, 7.0 and 9.0) no hydrolysis was observed (as concluded from the measured methanol concentration, see table under "Any other information on results incl. tables"), the main study did not need to be conducted according to OECD 111.
- Validity criteria fulfilled:
- yes
- Conclusions:
- In the preliminary study at 50°C and applied buffer pH-values of 4.0, 7.0 and 9.0 no hydrolysis (< 1%) could be observed during the 9 days of the experiment. The submission substance is regarded hydrolytically stable under normal environmental conditions.
- Executive summary:
The abiotic degradation of the submission substance was determined according to EU method C.7 and in accordance with OECD-Guideline 111.
The rate of degradation was measured at three different pH-values (4, 7, and 9). At all tested pH values the test substance was stable, this means that the degradation was less than 10 % after 5 days at 50°C. Therefore no further testing was necessary according to the guidelines mentioned above.
Because the test substance is nearly insoluble in aqueous solutions and in common organic solvents, it was impossible to prepare defined solutions. Therefore suspensions of the test substance in the single buffer solutions with a nominal concentration of approximately 2 g/L (4 mmol/L) were prepared.
Due to the test substance properties no analytical method was available for the direct determination of the pigment concentration. Therefore the observation of the degradation progress was achieved by determination of the concentration of methanol, which is the predicted degradation product (ester hydrolysis)
The test suspensions were incubated at 50°C over a period of 217.5 hours (approx. 9 days). Samples were taken from time to time and the methanol concentration was determined by GC-analysis.
All analyzed samples had a methanol concentration below 1 mg/L. This corresponds with a degree of hydrolysis below 1%.
Summing up, the measured results showed that the submission substance is hydrolytically stable at the tested pH-values 4, 7 and 9.
No further testing according to the mentioned guidelines has to be performed.
- Endpoint:
- hydrolysis
- Type of information:
- read-across from supporting substance (structural analogue or surrogate)
- Adequacy of study:
- key study
- Justification for type of information:
- see attachment
- Reason / purpose for cross-reference:
- read-across source
- GLP compliance:
- not specified
- Analytical monitoring:
- yes
- Duration:
- 217.5 h
- pH:
- 4
- Temp.:
- 50 °C
- Initial conc. measured:
- 2.235 g/L
- Remarks:
- the value represents the nominal concentration (4.93 mmol/L)
- Duration:
- 217.5 h
- pH:
- 7
- Temp.:
- 50 °C
- Initial conc. measured:
- 2.024 g/L
- Remarks:
- the value represents the nominal concentration (4.46 mmol/L)
- Duration:
- 217.5 h
- pH:
- 9
- Temp.:
- 50 °C
- Initial conc. measured:
- 1.849 g/L
- Remarks:
- the value represents the nominal concentration (4.08 mmol/L)
- Number of replicates:
- One
- Positive controls:
- no
- Negative controls:
- no
- Transformation products:
- no
- Details on hydrolysis and appearance of transformation product(s):
- No hydrolysis observed.
- pH:
- 4
- Temp.:
- 50 °C
- Remarks on result:
- hydrolytically stable based on preliminary test
- pH:
- 7
- Temp.:
- 50 °C
- Remarks on result:
- hydrolytically stable based on preliminary test
- pH:
- 9
- Temp.:
- 50 °C
- Remarks on result:
- hydrolytically stable based on preliminary test
- Details on results:
- As in the preliminary study at 50°C at all three pH-values (4.0, 7.0 and 9.0) no hydrolysis was observed, the main study did not need to be conducted according to OECD 111.
- Validity criteria fulfilled:
- yes
- Conclusions:
- In the preliminary study at 50°C and applied buffer pH-values of 4.0, 7.0 and 9.0 no hydrolysis (< 1%) could be observed during the 9 days of the experiment. The submission substance is regarded hydrolytically stable under normal environmental conditions.
Referenceopen allclose all
Results of preliminary test:
Tested |
Sample |
Duration of |
Measured |
Hydrolyzed [%] |
pH-value |
Results |
|
Start |
0.0 |
< 1 mg/I |
< 1.0 |
4.0 |
No further |
|
E1 |
25.3 |
< 1 mg/I |
< 1.0 |
4.0 |
testing necessary |
4.0 |
E2 |
49.5 |
< 1 mg/I |
< 1.0 |
4.0 |
degradation <10% (5 days) |
|
E3 |
97.2 |
< 1 mg/I |
< 1.0 |
4.0 |
Theoretical Me0H |
|
E4 |
169.3 |
< 1 mg/I |
< 1.0 |
4.3 |
concentration at 10% |
|
E5 |
217.5 |
< 1 mg/I |
< 1.0 |
4.0 |
degradation = 15.8 mg/L |
|
Start |
0.0 |
< 1 mg/I |
< 1.0 |
7.0 |
No further |
|
E1 |
25.4 |
< 1 mg/I |
< 1.0 |
7.0 |
testing necessary |
7.0 |
E2 |
49.5 |
< 1 mg/I |
< 1.0 |
7.0 |
degradation <10% (5 days) |
|
E3 |
97.4 |
< 1 mg/I |
< 1.0 |
7.0 |
Theoretical Me0H |
|
E4 |
169.5 |
< 1 mg/I |
< 1.0 |
7.0 |
concentration at 10% |
|
E5 |
217.5 |
< 1 mg/I |
< 1.0 |
7.0 |
degradation = 14.3 mg/L |
|
Start |
0.0 |
< 1 mg/I |
< 1.0 |
9.0 |
No further |
|
E1 |
25.7 |
< 1 mg/I |
< 1.0 |
9.0 |
testing necessary |
9.0 |
E2 |
49.5 |
< 1 mg/I |
< 1.0 |
9.0 |
degradation <10% (5 days) |
|
E3 |
97.5 |
< 1 mg/I |
< 1.0 |
9.0 |
Theoretical Me0H |
|
E4 |
169.5 |
< 1 mg/I |
< 1.0 |
9.0 |
concentration at 10% |
|
E5 |
217.5 |
< 1 mg/I |
< 1.0 |
9.0 |
degradation = 13.1 mg/L |
Description of key information
A hydrolysis study according to OECD 111 was performed with C.I. Pigment Yellow 175, which exhibits the highest water solubility within the group of the Acetolone pigments. In addition, there are functional groups present in the molecule of PY 175, which can be hydrolyzed from a theoretical point of view. PY 175 was stable at all tested pH values
Read-across to PY 194 bulk form is justified since the water solubility is much lower and there are no ester functions present in the molecule.
Key value for chemical safety assessment
Additional information
Information on Registered Substances comes from registration dossiers which have been assigned a registration number. The assignment of a registration number does however not guarantee that the information in the dossier is correct or that the dossier is compliant with Regulation (EC) No 1907/2006 (the REACH Regulation). This information has not been reviewed or verified by the Agency or any other authority. The content is subject to change without prior notice.
Reproduction or further distribution of this information may be subject to copyright protection. Use of the information without obtaining the permission from the owner(s) of the respective information might violate the rights of the owner.