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EC number: 276-344-2 | CAS number: 72102-84-2
- 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
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- guideline study with acceptable restrictions
- Qualifier:
- according to guideline
- Guideline:
- other: Deutsche Einhheitsverfahren DEV H-5
- Deviations:
- yes
- Remarks:
- see "Principles of method if other than guideline"
- Principles of method if other than guideline:
- Instead of testing various dilutions of a waste-water the test substance was tested in 5 concentrations chosen on the basis of the TOD (Theoretical Oxygen Demand).
- GLP compliance:
- no
- Oxygen conditions:
- aerobic
- Inoculum or test system:
- activated sludge, industrial, non-adapted
- Details on inoculum:
- Polyvalent waste-water bacteria collected on February 18, 1981, in the aeration unit of the sewage treatment plant of Rheinfelden (Switzerland).
- Duration of test (contact time):
- 5 d
- Initial conc.:
- > 1 - < 5 mg/L
- Based on:
- test mat.
- Parameter followed for biodegradation estimation:
- O2 consumption
- Details on study design:
- - Vessels: 100 mL BOD-flasks
- Test concentrations: Blank, 1, 2, 3, 4, 5 mg/L
- Test medium:
- 8.5 mg KH2PO4
- 21.75 mg K2HPO4
- 33.4 mg NaHPO4
- 1.7 mg NH4CI
- 22.5 mg MgSO4.7H2O
- 27.5 mg CaCl2.2H2O
- 0.25 mg FeCl3.6H2O
- Temperature: 20±1 °C
- Measurement : Oxygen concentration in mg/L with ORION-Electrode Type 97-08 - Reference substance:
- benzoic acid, sodium salt
- Test performance:
- No abnormalities were seen during the performance of the test.
- Key result
- Parameter:
- % degradation (O2 consumption)
- Value:
- 0
- Sampling time:
- 5 d
- Details on results:
- A BOD5 value of 0 mg O2/ mg test substance was observed at all tested concenterations. The TOD was calculated to be 0.384 mg O2/mg test substance.
- Parameter:
- BOD5
- Value:
- 0 mg O2/g test mat.
- Results with reference substance:
- The BOD value for the reference substance (sodium benzoate) was measured with 1.275 mg Oxygen/mg (equal to 95.8 % Biodegradation).
- Validity criteria fulfilled:
- yes
- Interpretation of results:
- under test conditions no biodegradation observed
- Conclusions:
- The test substance is not readily biodegradable.
- Endpoint:
- biodegradation in water: ready biodegradability
- Type of information:
- (Q)SAR
- Adequacy of study:
- weight of evidence
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- results derived from a valid (Q)SAR model, but not (completely) falling into its applicability domain, with adequate and reliable documentation / justification
- Justification for type of information:
- Please refer to the QMRF and QPRF files provided under the section attached justification.
- Principles of method if other than guideline:
- Estimation of results of OECD screening tests on ready biodegradation in water: CATALOGIC (v5.13.1.156) BOD 28 days MITI (OECD 301C) v11.15)
- GLP compliance:
- no
- Oxygen conditions:
- aerobic
- Inoculum or test system:
- activated sludge, domestic, non-adapted
- Duration of test (contact time):
- 28 d
- Key result
- Parameter:
- % degradation (O2 consumption)
- Value:
- ca. 10
- Sampling time:
- 28 d
- Details on results:
- Model domain similarity:
- Parametric domain: 100%
- Structural domain: 65% (35% unknown)
- Mechanistic domain: 100% - Interpretation of results:
- other: not readily biodegradable (according to OECD criteria)
- Endpoint:
- biodegradation in water: ready biodegradability
- Type of information:
- (Q)SAR
- Adequacy of study:
- weight of evidence
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- results derived from a valid (Q)SAR model and falling into its applicability domain, with adequate and reliable documentation / justification
- Justification for type of information:
- Please refer to the QMRF and QPRF files provided under the section attached justification.
- Principles of method if other than guideline:
- Prediction of ready biodegradability based on six QSAR models
- GLP compliance:
- no
- Oxygen conditions:
- aerobic
- Duration of test (contact time):
- 28 d
- Key result
- Parameter:
- other: biodegradation
- Sampling time:
- 28 d
- Remarks on result:
- other: Biowin1: Does Not Biodegrade Fast; Biowin2: Does Not Biodegrade Fast; Biowin3: Months; Biowin4: Days-Weeks; Biowin5: Does Not Biodegrade Fast; Biowin6: Does Not Biodegrade Fast; Biowin7: Does Not Biodegrade Fast; Ready Biodegradability Prediction: NO
- Interpretation of results:
- other: not readily biodegradable
Referenceopen allclose all
BIOWIN v4.10 Results
Biowin1 (Linear Model Prediction): Does Not Biodegrade Fast
Biowin2 (Non-Linear Model Prediction): Does Not Biodegrade Fast
Biowin3 (Ultimate Biodegradation Timeframe): Months
Biowin4 (Primary Biodegradation Timeframe): Days-Weeks
Biowin5 (MITI Linear Model Prediction): Does Not Biodegrade Fast
Biowin6 (MITI Non-Linear Model Prediction): Does Not Biodegrade Fast
Biowin7 (Anaerobic Model Prediction): Does Not Biodegrade Fast
Ready Biodegradability Prediction: NO
TYPE |
NUM |
Biowin1 FRAGMENT DESCRIPTION |
COEFF |
VALUE |
Frag |
1 |
Alkyl substituent on aromatic ring |
0.0547 |
0.0547 |
Frag |
1 |
Azo group [-N=N-] |
-0.2418 |
-0.2418 |
MolWt |
* |
Molecular Weight Parameter |
|
-0.1439 |
Const |
* |
Equation Constant |
|
0.7475 |
RESULT |
Biowin1 (Linear Biodeg Probability) |
0.4165 |
TYPE |
NUM |
Biowin2 FRAGMENT DESCRIPTION |
COEFF |
VALUE |
Frag |
1 |
Alkyl substituent on aromatic ring |
0.5771 |
0.5771 |
Frag |
1 |
Azo group [-N=N-] |
-8.2194 |
-8.2194 |
MolWt |
* |
Molecular Weight Parameter |
|
-4.2920 |
RESULT |
Biowin2 (Non-Linear Biodeg Probability) |
0.0001 |
||
|
A Probability Greater Than or Equal to 0.5 indicates --> Biodegrades Fast
A Probability Less Than 0.5 indicates --> Does NOT Biodegrade Fast
TYPE |
NUM |
Biowin3 FRAGMENT DESCRIPTION |
COEFF |
VALUE |
Frag |
1 |
Alkyl substituent on aromatic ring |
-0.0749 |
-0.0749 |
Frag |
1 |
Azo group [-N=N-] |
-0.3004 |
-0.3004 |
MolWt |
* |
Molecular Weight Parameter |
|
-0.6679 |
Const |
* |
Equation Constant |
|
3.1992 |
RESULT |
Biowin3 (Survey Model - Ultimate Biodeg) |
2.1560 |
TYPE |
NUM |
Biowin4 FRAGMENT DESCRIPTION |
COEFF |
VALUE |
Frag |
1 |
Alkyl substituent on aromatic ring |
-0.0685 |
-0.0685 |
Frag |
1 |
Azo group [-N=N-] |
-0.0528 |
-0.0528 |
MolWt |
* |
Molecular Weight Parameter |
|
-0.4361 |
Const |
* |
Equation Constant |
|
3.8477 |
RESULT |
Biowin4 (Survey Model - Primary Biodeg) |
3.2903 |
Result Classification: 5.00 -> hours 4.00 -> days 3.00 -> weeks
(Primary & Ultimate) 2.00 -> months 1.00 -> longer
TYPE |
NUM |
Biowin5 FRAGMENT DESCRIPTION |
COEFF |
VALUE |
Frag |
1 |
Azo group [-N=N-] |
-0.0459 |
-0.0459 |
Frag |
1 |
Aromatic-CH3 |
0.0415 |
0.0415 |
Frag |
2 |
Aromatic-H |
0.0082 |
0.0164 |
Frag |
1 |
-CH - [cyclic] |
0.0124 |
0.0124 |
MolWt |
* |
Molecular Weight Parameter |
|
-0.8992 |
Const |
* |
Equation Constant |
|
0.7121 |
RESULT |
Biowin5 (MITI Linear Biodeg Probability) |
-0.1626 |
TYPE |
NUM |
Biowin6 FRAGMENT DESCRIPTION |
COEFF |
VALUE |
Frag |
1 |
Azo group [-N=N-] |
-10.6129 |
-10.6129 |
Frag |
1 |
Aromatic-CH3 |
0.3072 |
0.3072 |
Frag |
2 |
Aromatic-H |
0.1201 |
0.2403 |
Frag |
1 |
-CH - [cyclic] |
-0.1295 |
-0.1295 |
MolWt |
* |
Molecular Weight Parameter |
|
-8.7256 |
RESULT |
Biowin6 (MITI Non-Linear Biodeg Probability) |
0.0000 |
A Probability Greater Than or Equal to 0.5 indicates --> Readily Degradable
A Probability Less Than 0.5 indicates --> NOT Readily Degradable
TYPE |
NUM |
Biowin7 FRAGMENT DESCRIPTION |
COEFF |
VALUE |
Frag |
1 |
Alkyl substituent on aromatic ring |
-0.1145 |
-0.1145 |
Frag |
1 |
Azo group [-N=N-] |
0.0000 |
0.0000 |
Frag |
1 |
Aromatic-CH3 |
-0.2573 |
-0.2573 |
Frag |
2 |
Aromatic-H |
-0.0954 |
-0.1909 |
Frag |
1 |
-CH - [cyclic] |
0.0395 |
0.0395 |
Const |
* |
Equation Constant |
|
0.8361 |
RESULT |
Biowin7 (Anaerobic Linear Biodeg Prob) |
0.3129 |
A Probability Greater Than or Equal to 0.5 indicates --> Biodegrades Fast
A Probability Less Than 0.5 indicates --> Does NOT Biodegrade Fast
Ready Biodegradability Prediction: (YES or NO)
----------------------------------------------
Criteria for the YES or NO prediction: If the Biowin3 (ultimate survey
model) result is "weeks" or faster (i.e. "days", "days to weeks", or
"weeks" AND the Biowin5 (MITI linear model) probability is >= 0.5, then
the prediction is YES (readily biodegradable). If this condition is not
satisfied, the prediction is NO (not readily biodegradable). This method
is based on application of Bayesian analysis to ready biodegradation data
(see Help). Biowin5 and 6 also predict ready biodegradability, but for
degradation in the OECD301C test only; using data from the Chemicals
Evaluation and Research Institute Japan (CERIJ) database.
Description of key information
The test substance is not readily biodegradable according OECD criteria.
Key value for chemical safety assessment
Additional information
In Article 13 of Regulation (EC) No 1907/2006, it is laid down that information on intrinsic properties of substances may be generated by means other than tests, provided that the conditions set out in Annex XI (of the same Regulation) are met. Furthermore according to Article 25 of the same Regulation testing on vertebrate animals shall be undertaken only as a last resort.
According to Annex XI of Regulation (EC) No 1907/2006 (Q)SAR results can be used if (1) the scientific validity of the (Q)SAR model has been established, (2) the substance falls within the applicability domain of the (Q)SAR model, (3) the results are adequate for the purpose of classification and labeling and/or risk assessment and (4) adequate and reliable documentation of the applied method is provided.
For the assessment of the test substance (Q)SAR results were used for aerobic biodegradability in water.The criteria listed in Annex XI of Regulation (EC) No 1907/2006 are considered to be adequately fulfilled and therefore the endpoint(s) sufficiently covered and suitable for risk assessment.
Therefore, further experimental studies on aerobic biodegradability in water are not provided.
Both QSAR models show that the test substance is not readily biodegradable according OECD criteria. The EPI Suite v4.10 (BIOWIN Program v4.10) calculation resulted in "not readily biodegradable". The test substance was within the applicability domain of the model. Additionally, the biodegradation was calculated by using CATALOGIC v5.13.1.156 (BOD 28 days MITI (OECD 301C) v11.15. It resulted in 10 % biodegradation after 28 d. Even though the structural domain was correct with only 65 % (35 % unknown) the results support the overall conclusion in the weight of evidence. Furthermore, none of the predicted metabolites are relevant for the subsequent PBT/vPvB assessment as they are either readily biodegradable or have logKow values << 4 which is indicative of a negligible potential to bioaccumulate.
ID | Quantity [%] | LogKow | Smiles | BOD [%] |
parent | 0.3783 | 0.4982 | Cc1cc2c(cc1N=NC1C(=O)NC(=O)NC1=O)NC(=O)N2 | 10 |
metabolite | 7.877 | 0.8346 | Cc1cc2c(cc1N)NC(=O)N2 | 0 |
metabolite | 0.2785 | -1.9933 | NC1C(=O)NC(=O)NC1=O | 65 |
metabolite | 60.79 | 0.5016 | Cc1cc2c(cc1N=NC(C(O)=O)C(O)=O)NC(=O)N2 | 1 |
metabolite | 6.333 | -1.5553 | NC(N)=O | 81 |
metabolite | 25.12 | -0.1608 | Cc1cc2c(cc1N=NC(C(N)=O)C(O)=O)NC(=O)N2 | 3 |
metabolite | 5.728 | -0.4342 | Cc1cc2c(cc1N=NC(C(N)=O)C(N)=O)NC(=O)N2 | 6 |
metabolite | 2.501 | -4.8137 | NC(C(O)=O)C(O)=O | 58 |
metabolite | 0.3809 | -5.0761 | NC(C(N)=O)C(O)=O | 40 |
metabolite | 0.4656 | -1.0365 | OC(=O)C(=O)C(O)=O | 90 |
metabolite | 0.2729 | -1.6989 | NC(=O)C(=O)C(O)=O | 53 |
metabolite | 1.008 | -1.4027 | OC(=O)C=O | 100 |
Moreover, the pigment is practically insoluble and therefore considered to be essentially not bioavailable. Due to the large molecular size, cellular uptake of the pigment is unlikely. Hence intracellular biodegradation, which is the main degradation route of bacteria, is probably low. It can be concluded that the substance is likely to persist in the environment. For this reason no ready or inherent degradation studies are proposed.
Additionally, the weight-of-evidence is supported by the estimation of the BOD5 (CIBA-GEIGY Limited 1981). It was tested according to the German Guideline H-5. In this study concentrations of 1, 2, 3, 4 and 5 mg/L of test substance, a negative and a positive control (sodium benzoate) were tested. No biodegradation was observed during the exposure period of 5 days. The BOD5 for the test substance was 0 mg O2/mg test substance, and the TOD was 0.384 mg O2/mg test substance. The BOD5 for the reference substance was measured at 1.275 mg O2/mg which is equal to 95.8% biodegradation.
In overall conclusion, further tests on biodegradation are scientifically not justified.
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.
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