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EC number: 217-568-2 | CAS number: 1889-67-4
- 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
Bioaccumulation: aquatic / sediment
Administrative data
Link to relevant study record(s)
- Endpoint:
- bioaccumulation in aquatic species: fish
- Data waiving:
- other justification
- Justification for data waiving:
- other:
- Endpoint:
- bioaccumulation in aquatic species: fish
- Type of information:
- (Q)SAR
- Adequacy of study:
- supporting study
- Study period:
- 2019
- Reliability:
- 1 (reliable without restriction)
- 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.
- Qualifier:
- according to guideline
- Guideline:
- other: REACH Guidance on QSAR R.6
- Principles of method if other than guideline:
- Estimation of BCF using T.E.S.T. v4.2.1
- GLP compliance:
- no
- Specific details on test material used for the study:
- SMILES: CC(C)(c1ccccc1)C(C)(C)c2ccccc2
- Test organisms (species):
- other: fish
- Details on estimation of bioconcentration:
- BASIS FOR CALCULATION OF BCF
- Estimation software: US EPA T.E.S.T. v4.2.1
Applied estimation methods:
- Hierarchical method : The toxicity for a given query compound is estimated using the weighted average of the predictions from several different cluster models.
- FDA method : The prediction for each test chemical is made using a new model that is fit to the chemicals that are most similar to the test compound. Each model is generated at runtime.
- Single model method : Predictions are made using a multilinear regression model that is fit to the training set (using molecular descriptors as independent variables).
- Group contribution method : Predictions are made using a multilinear regression model that is fit to the training set (using molecular fragment counts as independent variables).
- Nearest neighbor method : The predicted toxicity is estimated by taking an average of the 3 chemicals in the training set that are most similar to the test chemical.
- Consensus method : The predicted toxicity is estimated by taking an average of the predicted toxicities from the above QSAR methods (provided the predictions are within the respective applicability domains; recommended method by T.E.S.T. for providing the most accurate predictions). - Key result
- Type:
- BCF
- Value:
- 1 275.22 L/kg
- Remarks on result:
- other: method: consensus
- Type:
- other: logBCF
- Value:
- 3.11 dimensionless
- Remarks on result:
- other: method: consensus
- Validity criteria fulfilled:
- yes
- Conclusions:
- Using T.E.S.T. v4.2.1 the BCF value of the test item was calculated to be 1275. The substance is within the applicability domain of the model. Thus, the estimation is considered to be accurate.
- Executive summary:
The BCF value was calculated using T.E.S.T v4.2.1 from US Environmental Protection Agency. The BCF value of the test item was calculated to be 1275 L/kg.
The adequacy of a prediction depends on the following conditions:
a) the (Q)SAR model is scientifically valid: the scientific validity is established according to the OECD principles for (Q)SAR validation;
b) the (Q)SAR model is applicable to the query chemical: a (Q)SAR is applicable if the query chemical falls within the defined applicability domain of the model;
c) the (Q)SAR result is reliable: a valid (Q)SAR that is applied to a chemical falling within its applicability domain provides a reliable result;
d) the (Q)SAR model is relevant for the regulatory purpose.
For assessment and justification of these 4 requirements the QMRF and QPRF files were developed and attached to this study record.
Description of the prediction Model
The prediction model was descripted using the harmonised template for summarising and reporting key information on (Q)SAR models. For more details please refer to the attached QSAR Model Reporting Format (QMRF) file.
Assessment of estimation domain
The assessment of the estimation domain was documented in the QSAR Prediction Reporting Format file (QPRF). Please refer to the attached document for the details of the prediction and the assessment of the estimation domain.
- Endpoint:
- bioaccumulation: aquatic / sediment
- Type of information:
- (Q)SAR
- Adequacy of study:
- supporting study
- Study period:
- 2019
- Reliability:
- 1 (reliable without restriction)
- 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.
- Qualifier:
- according to guideline
- Guideline:
- other: REACH Guidance on QSAR R.6
- Principles of method if other than guideline:
- Estimation of BCF using VEGA v1.1.4 BCF model CAESAR v2.1.14
- GLP compliance:
- no
- Specific details on test material used for the study:
- SMILES: CC(C)(c1ccccc1)C(C)(C)c2ccccc2
- Test organisms (species):
- other: fish
- Details on estimation of bioconcentration:
- BASIS INFORMATION
- Measured/calculated logPow: calculated
BASIS FOR CALCULATION OF BCF
- Estimation software: VEGA CAESAR v2.1.14
- Result based on calculated log Pow of: 5.4 (calculated by VEGA) - Key result
- Type:
- BCF
- Value:
- 999 L/kg
- Remarks on result:
- other: QSAR predicted value. The substance is within the applicability domain of the model. According to the model’s global AD index, the predicted substanceis into the Applicability Domain of the model.
- Type:
- other: logBCF
- Value:
- 3 dimensionless
- Remarks on result:
- other: QSAR prediction value.
- Validity criteria fulfilled:
- yes
- Conclusions:
- Using CAESAR v2.1.14 the BCF value of the test item was calculated to be 999 L/kg. The substance is within the applicability domain of the model. Thus, the estimation is considered to be accurate.
- Executive summary:
The BCF value was calculated using CAESAR v2.1.14 as part of VEGA v1.1.4 from IRCCS - Istituto di Ricerche Farmacologiche Mario Negri.
The BCF value of the test item was calculated to be 999 L/kg (VEGA, 2017).
The adequacy of a prediction depends on the following conditions:
a) the (Q)SAR model is scientifically valid: the scientific validity is established according to the OECD principles for (Q)SAR validation;
b) the (Q)SAR model is applicable to the query chemical: a (Q)SAR is applicable if the query chemical falls within the defined applicability domain of the model;
c) the (Q)SAR result is reliable: a valid (Q)SAR that is applied to a chemical falling within its applicability domain provides a reliable result;
d) the (Q)SAR model is relevant for the regulatory purpose.
For assessment and jsutification of these 4 requirements the QMRF and QPRF files were developed and attached to this study record.
Description of the prediction Model
The prediction model was descripted using the harmonised template for summarising and reporting key information on (Q)SAR models. For more details please refer to the attached QSAR Model Reporting Format (QMRF) file.
Assessment of estimation domain
The assessment of the estimation domain was documented in the QSAR Prediction Reporting Format file (QPRF). Please refer to the attached document for the details of the prediction and the assessment of the estimation domain.
Referenceopen allclose all
Table 1. QSAR Model results
Method |
Predicted value |
Model statistics |
MAE (in log10) |
||||||
External test set |
Training set |
||||||||
log BCF |
BCF |
r² |
q² |
No. of chemicals |
Entire set |
SC >= 0.5 |
Entire set |
SC >= 0.5 |
|
Consensus method |
3.11 |
1275.22 |
- |
- |
- |
0.51 |
0.43 |
0.42 |
0.52 |
Hierarchical clustering |
3.05 |
1120.10 (88.95-14104.75) |
0.748 – 0.853 |
0.715 – 0.817 |
223 - 540 (cluster models: 3) |
0.54 |
0.56 |
0.23 |
0.25 |
Single model |
3.13 |
1343.62 (100.31-17998.00) |
0.764 |
0.733 |
540 |
0.54 |
0.34 |
0.53 |
0.57 |
Group contribution |
3.74 |
5439.83 (226.11-130874.08) |
0.719 |
0.527 |
499 |
0.62 |
0.59 |
0.60 |
0.64 |
FDA |
2.81 |
642.20 (100.83-4090.12) |
0.682 |
0.608 |
40 |
0.57 |
0.52 |
0.53 |
0.71 |
Nearest neighbor |
2.81 |
641.41 |
- |
- |
3 |
0.60 |
0.76 |
0.55 |
0.55 |
The substance is within the applicability domain of the Hierarchical clustering method. Based on the mean absolute error for the external test set, the confidence in the predicted BCF values is low.
The substance is within the applicability domain of the FDA method. Based on the mean absolute error for the external test set, the confidence in the predicted BCF values is high.
The substance is within the applicability domain of the Single model method. Based on the mean absolute error for the external test set, the confidence in the predicted BCF values is high.
The substance is within the applicability domain of the Group contribution method. Based on the mean absolute error for the external test set, the confidence in the predicted BCF values is high.
The substance is within the applicability domain of the Nearest neighbor method. Based on the mean absolute error for the external test set, the confidence in the predicted BCF values is low.
The substance is within the applicability domain of the Consensus method. Based on the mean absolute error for the external test set, the confidence in the predicted BCF values is high.
According to the model’s global AD index, the predicted substance is in the Applicability Domain of the model.
Compound: Molecule 0
Compound SMILES: c1ccc(cc1)C(C)(C)C(c2ccccc2)(C)C
Experimental value [log(L/kg)]: -
Predicted BCF [log(L/kg)]: 3
Predicted BCF [L/kg]: 999
Predicted BCF from sub-model 1 (HM) [log(L/kg)]: 3.01
Predicted BCF from sub-model 2 (GA) [log(L/kg)]: 2.81
Predicted LogP (MLogP): 5.4
Structural alerts: -
Reliability: the predicted compound is into the Applicability Domain of the model
Remarks:
none
Description of key information
The performance of a test for bioaccumulation in aquatic species, preferably fish, has been requested in decision CCH-D-2114543301-63-01/F and is currently ongoing. The endpoint will be updated with the new information by the set deadline in the final decision.
Using VEGA v1.1.4 model CAESAR v2.1.14 the BCF value of the test item was calculated to be 999 L/kg. Using T.E.S.T. v4.2.1 the BCF value of the test item was calculated to be 1275 L/kg. The substance is within the applicability domain of both models. Thus, the estimations are considered to be accurate. For risk assessment purposes as worst case scenario the value of 1275 L/kg was chosen as a key value.
Key value for chemical safety assessment
- BCF (aquatic species):
- 1 275 L/kg ww
Additional information
The performance of a test for bioaccumulation in aquatic species, preferably fish, is currently ongoing. As supporting information, two QSAR calculations have been performed. The higher BCF value is used for risk assessment purposes until the experimental study is finalised.
The adequacy of a prediction depends on the following conditions:
a) the (Q)SAR model is scientifically valid: the scientific validity is established according to the OECD principles for (Q)SAR validation;
b) the (Q)SAR model is applicable to the query chemical: a (Q)SAR is applicable if the query chemical falls within the defined applicability domain of the model;
c) the (Q)SAR result is reliable: a valid (Q)SAR that is applied to a chemical falling within its applicability domain provides a reliable result;
d) the (Q)SAR model is relevant for the regulatory purpose.
For assessment and justification of these 4 requirements the QMRF and QPRF files were developed and attached to this study record.
Description of the prediction Model
The prediction model was descripted using the harmonised template for summarising and reporting key information on (Q)SAR models. For more details please refer to the attached QSAR Model Reporting Format (QMRF) file.
Assessment of estimation domain
The assessment of the estimation domain was documented in the QSAR Prediction Reporting Format file (QPRF). Please refer to the attached document for the details of the prediction and the assessment of the estimation domain.
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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