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Diss Factsheets
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EC number: 406-040-9 | CAS number: 125643-61-0
- 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
Bioaccumulation: aquatic / sediment
Administrative data
- Endpoint:
- bioaccumulation: aquatic / sediment
- Type of information:
- (Q)SAR
- Adequacy of study:
- key study
- Study period:
- August 2012
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- other: see 'Remark'
- Remarks:
- The substance is a UVCB of low solubility in water. As such, it is not possible to accurately conduct a bioaccumulation study for the material. In addition, the substance is subject to hydrolysis at biologically relevant pH’s (4 and 9). It is anticipated that bioaccumulation of the substance itself would not occur, as hydrolytic effects in association with metabolic effects would result in removal of the substance. To this end, and evaluation of bioaccumulation potential utilising in silico techniques is considered appropriate in this instance.
- Justification for type of information:
- QSAR prediction: migrated from IUCLID 5.6
Data source
Reference
- Reference Type:
- other company data
- Title:
- Unnamed
- Report date:
- 2013
Materials and methods
Test guideline
- Qualifier:
- no guideline followed
- Principles of method if other than guideline:
- The registrant has undertaken an assessment of bioaccumulation potential, using the US EPA BCFBAF v3.01 programme .
- GLP compliance:
- no
- Remarks:
- Conducted in compliance with ISO 9001 accreditation
Test material
- Reference substance name:
- -
- EC Number:
- 406-040-9
- EC Name:
- -
- Cas Number:
- 125643-61-0
- Molecular formula:
- C17 H25 O3 R, Where R = (C7 H15) or (C8 H17) or (C9 H19)
- IUPAC Name:
- Reaction mass of C7-9-alkyl 3-(3,5-di-trans-butyl-4-hydroxyphenyl)propionate
- Test material form:
- liquid: viscous
- Details on test material:
- Not applicable - QSAR evaluation
Constituent 1
- Specific details on test material used for the study:
- Details on properties of test surrogate or analogue material (migrated information):
Not applicable - QSAR evaluation - Radiolabelling:
- no
Sampling and analysis
- Details on sampling:
- Not applicable - QSAR evaluation
Test solutions
- Vehicle:
- no
- Details on preparation of test solutions, spiked fish food or sediment:
- Not applicable - QSAR evaluation
Test organisms
- Test organisms (species):
- other: Not applicable - QSAR evaluation
- Details on test organisms:
- Not applicable - QSAR evaluation
Study design
- Route of exposure:
- other: Not applicable - QSAR evaluation
- Test type:
- other: Not applicable - QSAR evaluation
- Water / sediment media type:
- not specified
Test conditions
- Hardness:
- Not applicable - QSAR evaluation
- Test temperature:
- Not applicable - QSAR evaluation
- pH:
- Not applicable - QSAR evaluation
- Dissolved oxygen:
- Not applicable - QSAR evaluation
- TOC:
- Not applicable - QSAR evaluation
- Salinity:
- Not applicable - QSAR evaluation
- Details on test conditions:
- Please refer to QPRF appended below
- Nominal and measured concentrations:
- Not applicable - QSAR evaluation
- Reference substance (positive control):
- not required
- Details on estimation of bioconcentration:
- The registrant has undertaken an assessment of bioaccumulation potential, as the value for partition coefficient is not considered to be reflective of the potential for the substance to bioaccumulate in this case, and testing of this poorly soluble UVCB substance for the bioaccumulation endpoint is not considered relevant. The substance has been demonstrated to have a very high partition coefficient value. However, the high log Pow is considered to be more a consequence of poor water solubility issues than a lipophilic tendency and is considered to be not indicative of the tendency to bioaccumulate in lipid tissues of aquatic organisms. This is based on literature data which demonstrates a tendency for the Bioconcentration Factor (BCF) to decrease as Log Pow increases above 6. At a high value of 10, the substance is proposed not to bioaccumulate. This is further confirmed via the use of QSAR; use of the US EPA BCFBAF v3.01 programme for bioaccumulation indicates that the substance is unlikely to bioaccumulate, with calculated values used for the assessment of 6 different potential structures for C7, C8 and C9 components
Results and discussion
Bioaccumulation factoropen allclose all
- Type:
- BCF
- Value:
- >= 648.4 - <= 5 704 L/kg
- Basis:
- other: QSAR evaluation
- Calculation basis:
- other: QSAR
- Remarks on result:
- other: This result relates to the C7 derivative, where 6 potential analogues where assessed. This derivative is proposed to be ca. 9% w/w of the total product.
- Remarks:
- Conc.in environment / dose:Not applicable
- Type:
- BCF
- Value:
- >= 372.6 - <= 1 887 L/kg
- Basis:
- other: QSAR Evaluation
- Calculation basis:
- other: QSAR
- Remarks on result:
- other: This result relates to the C8 derivatives, where 6 potential analogues where assessed. These derivatives are proposed to be > 76% w/w of the total product.
- Remarks:
- Conc.in environment / dose:Not applicable
- Type:
- BCF
- Value:
- >= 123 - <= 1 178 L/kg
- Basis:
- other: QSAR Evaluation
- Calculation basis:
- other: QSAR
- Remarks on result:
- other: This result relates to the C9 derivatives, where 6 potential analogues where assessed. These derivatives are proposed to be ca 15% w/w of the total product.
- Remarks:
- Conc.in environment / dose:Not applicable
- Details on kinetic parameters:
- Not applicable - QSAR evaluation
- Metabolites:
- Not applicable - QSAR evaluation
- Results with reference substance (positive control):
- Not applicable - QSAR evaluation
- Details on results:
- Please see below under "any other information on results including tables.
- Reported statistics:
- Please refer to the QPRF document appended below.
Any other information on results incl. tables
The value for partition coefficient is not considered to be reflective of the potential for the substance to bioaccumulate in this case.The substance has been demonstrated to have a very high partition coefficient value. However, the high log Pow is considered to be more a consequence of poor water solubility issues than a lipophilic tendency and is considered to be not indicative of the tendency to bioaccumulate in lipid tissues of aquatic organisms. This is based on literature data which demonstrates a tendency for the Bioconcentration Factor (BCF) to decrease as Log Pow increases above 6. At a high value of 10, the substance is proposed not to bioaccumulate. This is further confirmed via the use of QSAR; use of the US EPA BCFBAF v3.01 programme for bioaccumulation indicates that the substance is unlikely to bioaccumulate, with calculated values used for the assessment of 6different potential structures for C7, C8 and C9 components as follows:
|
BCF value (L/kg wet-wt) |
Log BCF value |
C7 derivatives |
648.4 - 5704 |
2.812 – 3.756 |
C8 derivatives |
372.6 - 1887 |
2.571 – 3.276 |
C9 derivatives |
123 - 1178 |
2.090 – 3.071 |
As the majority of the substance does not fall into a BCF range where classification is applicable, it is proposed that bioaccumulation is not relevant for this substance.
Applicant's summary and conclusion
- Validity criteria fulfilled:
- yes
- Remarks:
- The substance fragments are considered to be within the range of the EPIWIN BCFBAF modelling software
- Conclusions:
- The value for partition coefficient is not considered to be reflective of the potential for the substance to bioaccumulate in this case. The substance has been demonstrated to have a very high partition coefficient value. However, the high log Pow is considered to be more a consequence of poor water solubility issues than a lipophilic tendency and is considered to be not indicative of the tendency to bioaccumulate in lipid tissues of aquatic organisms. This is based on literature data which demonstrates a tendency for the Bioconcentration Factor (BCF) to decrease as Log Pow increases above 6. At a high value of 10, the substance is proposed not to bioaccumulate. This is further confirmed via the use of QSAR; use of the US EPA BCFBAF v3.01 programme for bioaccumulation indicates that the substance is unlikely to bioaccumulate, with calculated values used for the assessment of 6 different potential structures for C7, C8 and C9 components.
As the majority of the substance does not fall into a BCF range where classification is applicable, it is proposed that bioaccumulation is not relevant for this substance. - Executive summary:
The value for partition coefficient is not considered to be reflective of the potential for the substance to bioaccumulate in this case. The substance has been demonstrated to have a very high partition coefficient value. However, the high log Pow is considered to be more a consequence of poor water solubility issues than a lipophilic tendency and is considered to be not indicative of the tendency to bioaccumulate in lipid tissues of aquatic organisms. This is based on literature data which demonstrates a tendency for the Bioconcentration Factor (BCF) to decrease as Log Pow increases above 6. At a high value of 10, the substance is proposed not to bioaccumulate. This is further confirmed via the use of QSAR; use of the US EPA BCFBAF v3.01 programme for bioaccumulation indicates that the substance is unlikely to bioaccumulate, with calculated values used for the assessment of 6 different potential structures for C7, C8 and C9 components.
As the majority of the substance does not fall into a BCF range where classification is applicable, it is proposed that bioaccumulation is not relevant for this substance.
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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