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Diss Factsheets
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EC number: 227-678-2 | CAS number: 5932-68-3
- 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
Short-term toxicity to aquatic invertebrates
Administrative data
Link to relevant study record(s)
- Endpoint:
- short-term toxicity to aquatic invertebrates
- Type of information:
- (Q)SAR
- Adequacy of study:
- key study
- Study period:
- From 2015-08-04 to 2015-08-05
- 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:
- 1. SOFTWARE
iSafeRat® HA-QSAR toolbox v2.1
2. MODEL (incl. version number)
iSafeRat® High Accuracy QSAR – version 1.5
3. SMILES OR OTHER IDENTIFIERS USED AS INPUT FOR THE MODEL
O(c(c(O)ccc1C=CC)c1)C
4. SCIENTIFIC VALIDITY OF THE (Q)SAR MODEL
See attached QMRF
5. APPLICABILITY DOMAIN
See attached QPRF
6. ADEQUACY OF THE RESULT
See attached QPRF - Qualifier:
- equivalent or similar to guideline
- Guideline:
- OECD Guideline 202 (Daphnia sp. Acute Immobilisation Test)
- Deviations:
- not applicable
- Remarks:
- (QSAR model)
- Qualifier:
- equivalent or similar to guideline
- Guideline:
- EU Method C.2 (Acute Toxicity for Daphnia)
- Deviations:
- not applicable
- Remarks:
- (QSAR model)
- Principles of method if other than guideline:
- The purpose of this QSAR model is to accurately predict the acute toxicity to daphnid as would be expected in a laboratory experiment following OECD Guideline 202 and EC method C.2 for specific, named modes of action to provide a value that can effectively replace a 48-hour EC50 value from an experimental study. The regression based method used to achieve this has been fully validated following the OECD (2004) recommendations (refer to the QMRF report with KREATiS identifier: KTS/QMRF/HOL/05 for further details).
- GLP compliance:
- no
- Specific details on test material used for the study:
- - Mode of action: MOA2, polar narcotic (alkyl/alkoxyphenols)
- Water solubility: 709 mg/L (from experimental study) - Analytical monitoring:
- no
- Details on sampling:
- Not applicable
- Vehicle:
- no
- Details on test solutions:
- Not applicable
- Test organisms (species):
- other: Daphnia magna, Daphnia pulex
- Details on test organisms:
- Results from the following species were used in the regression: Daphnia magna, Daphnia pulex.
Following the principles of Phase Equilibrium Thermodynamics, for narcotic substances, no difference in relationship between solubility and ecotoxicity between invertebrate (or indeed other) aquatic species is expected. Any observed differences may be attributed to lifestyle related parameters (e.g. shell closing in molluscs) and relative duration of study versus bodysize rather than to a specific toxic mechanism causing species differences. In this case, for MOA 2, no differences were observed in activity based toxicity for the 2 species used. - Test type:
- other: QSAR
- Water media type:
- freshwater
- Limit test:
- no
- Total exposure duration:
- 48 h
- Remarks on exposure duration:
- none
- Post exposure observation period:
- Not applicable
- Hardness:
- The QSAR is based on data from studies performed at acceptable hardness to ensure control survival.
- Test temperature:
- The temperatures varied from approximately 20 to 23 °C depending on the species used to construct the algorithm. This small difference is not expected to contribute to the variability of the EC50 values found in experimental data.
- pH:
- The QSAR is based on data from studies performed at acceptable pH between 6.0 - 9.0.
- Dissolved oxygen:
- The QSAR is based on data from studies performed at acceptable oxygen concentrations (generally >60%).
- Salinity:
- Not applicable.
- Nominal and measured concentrations:
- The QSAR is based on data from studies performed using measured concentrations or with acceptable stability.
- Details on test conditions:
- Not applicable
- Reference substance (positive control):
- no
- Remarks:
- QSAR model
- Key result
- Duration:
- 48 h
- Dose descriptor:
- EC50
- Effect conc.:
- 3 mg/L
- Nominal / measured:
- meas. (not specified)
- Conc. based on:
- test mat.
- Basis for effect:
- mobility
- Remarks on result:
- other: 95% CL:1.9-4.6 mg/L
- Details on results:
- The water solubility value given as input to the Ecotox module of the iSafeRat® Holistic HA-QSAR falls within the descriptor domain of the model between log water solubility (in log (mol/L)) of -5.06 to 0.109. Moreover the test substance is attributed to the class of polar narcotic compounds (MOA 2) as alkyl/alkoxy-phenol.
- Results with reference substance (positive control):
- Not applicable
- Reported statistics and error estimates:
- 95% CL: 1.9-4.6 mg/L
QSAR statistical parameters are given in the QMRF and the QPRF - Validity criteria fulfilled:
- yes
- Remarks:
- The substance falls into the applicability domains of the QSAR model.
- Conclusions:
- The 48-h EC50 based on mobility and measured concentrations was determined to be 3.0 mg/L with 95%-Confidence Limit between 1.9 and 4.6 mg/L.
- Executive summary:
A QSAR prediction was performed to assess the acute toxicity of the test substance to daphnid. This QSAR has been validated to be compliant with the OECD recommendations for QSAR modelling (OECD, 2004) and predicts the endpoint value which would be expected when testing the substance under experimental conditions in a laboratory following OECD Guideline 202. The criterion predicted was the EC50 (Median Effective Concentration), a statistically derived concentration which is expected to cause immobility in 50% of test animals within a period of 48 hours.
The immobility of the daphnids was determined using a validated QSAR for the Mode of Action in question, (MOA2, polar narcosis). The QSAR model is based on validated data for a training set of 19 chemicals derived from 48-hour tests on daphnids, for which the concentrations of the test substance had been determined by chemical analyses over the test period. The water solubility of the substance given as input was experimentally measured at 709 mg/L. The substance falls within the applicability domain of the model as demonstrated in the QPRF.
The 48-h EC50 based on mobility and measured concentrations was determined to be 3.0 mg/L with 95%-Confidence Limit between 1.9 and 4.6 mg/L.
- Endpoint:
- short-term toxicity to aquatic invertebrates
- Type of information:
- (Q)SAR
- Adequacy of study:
- key study
- Study period:
- Run on 2015/09
- 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 limited documentation / justification
- Justification for type of information:
- 1. SOFTWARE
ECOSAR
2. MODEL (incl. version number)
ECOSAR v1.11
3. SMILES OR OTHER IDENTIFIERS USED AS INPUT FOR THE MODEL
Oc(ccc1C=CC)c(c1)OC
log Kow: 2.1 (experimental result)
4. SCIENTIFIC VALIDITY OF THE (Q)SAR MODEL
- Defined endpoint: short term toxicity to aquatic invertebrates (Daphnid).
- Unambiguous algorithm: Linear regression QSAR; Log 48h-LC50 (mmol/L) = -0.5667*log Kow + 0.1481. To convert the LC50 from mmol/L to mg/L, multiply by the molecular weight.
- Defined domain of applicability: Applicable to chemicals with log Kow less than 7.0 and molecular weight less than 1000 g/mol. The model can be suitable for chemicals class of Phenols.
- Appropriate measures of goodness-of-fit and robustness and predictivity: N = 63+5 and the coefficient of determination R² = 0.7034.
- Mechanistic interpretation: related to the partitioning of the substance from water into the organisms lipid phase.
5. APPLICABILITY DOMAIN
Applicable to chemicals with log Kow less than 7.0 and molecular weight less than 1000 g/mol. The model can be suitable for chemicals class of Phenols.
6. ADEQUACY OF THE RESULT
The substance falls within the applicability domain described above and therefore the predicted value can be considered reliable.
For more information, see Phenols SAR document in "Attached background material". - Qualifier:
- according to guideline
- Guideline:
- other: REACH guidance on QSARs R.6, May 2008
- Deviations:
- no
- Principles of method if other than guideline:
- See attached QPRF.
- GLP compliance:
- no
- Remarks:
- (not relevant)
- Specific details on test material used for the study:
- - log Kow : 2.1 (experimental result)
- Details on sampling:
- Not applicable
- Details on test solutions:
- Not applicable
- Test organisms (species):
- Daphnia sp.
- Details on test organisms:
- None
- Test type:
- not specified
- Water media type:
- not specified
- Total exposure duration:
- 48 h
- Remarks on exposure duration:
- none
- Post exposure observation period:
- Not applicable
- Hardness:
- Not applicable
- Test temperature:
- Not applicable
- pH:
- Not applicable
- Dissolved oxygen:
- Not applicable
- Salinity:
- Not applicable
- Nominal and measured concentrations:
- Not applicable
- Details on test conditions:
- Not applicable
- Key result
- Duration:
- 48 h
- Dose descriptor:
- LC50
- Effect conc.:
- 7.5 mg/L
- Remarks on result:
- other: ECOSAR Class: Phenols
- Details on results:
- See QPRF report
- Results with reference substance (positive control):
- Not applicable
- Reported statistics and error estimates:
- N = 63+5 and the coefficient of determination R² = 0.7034.
- Validity criteria fulfilled:
- yes
- Conclusions:
- The substance was predicted to have a LC50 value at 7.5 mg/L to aquatic invertebrates Daphnid after 48h of exposure. The substance falls within the applicability domain and therefore the predicted value can be considered reliable.
- Executive summary:
The short term toxicity to daphnid was estimated using the ECOSAR v1.11 QSAR model available from the U.S. EPA.
The estimation 48h-LC50 was 7.5 mg/L (Phenols class), calculated from a measured log Kow value at 2.1 and a linear regression:
Log 48h-LC50 (mmol/L) = -0.5667*log Kow + 0.1481.
The substance falls within the applicability domain and therefore the predicted value can be considered reliable.
Referenceopen allclose all
No additional information
None
Description of key information
Geometric mean of QSARs models (iSafeRat v1.5 and ECOSAR v1.11):
48h-EC50 = 4.7 mg/L.
Key value for chemical safety assessment
Fresh water invertebrates
Fresh water invertebrates
- Effect concentration:
- 4.7 mg/L
Additional information
To assess the short-term toxicity of the registered substance to aquatic invertebrates, two reliable QSAR results are available.
The first prediction data (KREATiS, 2016) is a QSAR. This QSAR prediction (iSafeRat holistic approach v1.5) was performed on the registered substance, to assess the acute toxicity of the substance to daphnids. This QSAR has been validated to be compliant with the OECD recommendations for QSAR modelling (OECD, 2004) and predicts the endpoint value which would be expected when testing the substance under experimental conditions in a laboratory following OECD Guideline 202. The immobility of the daphnids was determined using a validated QSAR for the Mode of Action in question, (MOA 2, polar narcosis). This QSAR is based on validated data for a training set of 19 chemicals derived from 48-hour tests on daphnids, for which the concentrations of the test substance had been determined by chemical analyses over the test period. The substance falls within the applicability domain of the model. The 48h-EC50 value based on mobility and measured concentrations was determined to be 3.0 mg/L (95% CL: 1.9 - 4.6 mg/L).
The second prediction data (ECOSAR, 2015) is also a QSAR. This QSAR prediction used the ECOSAR v1.11 QSAR model available from the U.S. EPA to assess the acute toxicity of the registered substance to daphnids. The substance falls within the applicability domain of the model. The estimation 48h-EC50 was determined at 7.5 mg/L using the chemical class of Phenols.
In conclusion, according to these key data points, the key EC50 value on aquatic invertebrates, used for chemical safety assessment, is determined at 4.7 mg/L, corresponding to a geometric mean of predicted EC50 values.
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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