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Please be aware that this old REACH registration data factsheet is no longer maintained; it remains frozen as of 19th May 2023.
The new ECHA CHEM database has been released by ECHA, and it now contains all REACH registration data. There are more details on the transition of ECHA's published data to ECHA CHEM here.
Diss Factsheets
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EC number: 250-954-9 | CAS number: 32210-23-4
- 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: aquatic / sediment
- Type of information:
- (Q)SAR
- Adequacy of study:
- key study
- Study period:
- Run on 2013-04
- 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
- Remarks:
- The bioconcentration factor (BCF) of the substance was evaluated with the most recent model from BCFBAF model v3.01 from EPI Suite v4.1, which fulfilled all OECD principles. The substance is within the domain of the Arnot-Gobas BCFBAF model based on the fragments present in the BCFBAF database.
- Justification for type of information:
- QSAR prediction: migrated from IUCLID 5.6
- Qualifier:
- according to guideline
- Guideline:
- other: REACH guidance on QSARs R.6, May 2008
- Deviations:
- no
- Principles of method if other than guideline:
- See QMRF and QPRF in "Attached background material" and in "Any other information on materials and methods incl. tables" (the QMRF is only available for the former version of the QSAR model).
- GLP compliance:
- no
- Specific details on test material used for the study:
- - log Pow: 4.8 (experimental result)
- Radiolabelling:
- no
- Details on sampling:
- Not applicable
- Details on preparation of test solutions, spiked fish food or sediment:
- Not applicable
- Test organisms (species):
- no data
- Details on test organisms:
- Not applicable
- Test type:
- other: QSAR
- Water / sediment media type:
- not specified
- Hardness:
- Not applicable
- Test temperature:
- Not applicable
- pH:
- Not applicable
- Dissolved oxygen:
- Not applicable
- TOC:
- Not applicable
- Salinity:
- Not applicable
- Details on test conditions:
- Not applicable
- Nominal and measured concentrations:
- Not applicable
- Reference substance (positive control):
- no
- Details on estimation of bioconcentration:
- Not applicable
- Type:
- BCF
- Value:
- 234 L/kg
- Basis:
- whole body w.w.
- Remarks on result:
- other: Arnot-Gobas method, including biotransformation rate estimates, upper trophic. log BCF = 2.369
- Type:
- BCF
- Value:
- 309.2 L/kg
- Basis:
- whole body w.w.
- Remarks on result:
- other: Arnot-Gobas method, including biotransformation rate estimates, mid trophic. log BCF = 2.490
- Key result
- Type:
- BCF
- Value:
- 334.6 L/kg
- Basis:
- whole body w.w.
- Remarks on result:
- other: Arnot-Gobas method, including biotransformation rate estimates, lower trophic. log BCF = 2.524
- Details on kinetic parameters:
- Not applicable
- Metabolites:
- Not applicable
- Results with reference substance (positive control):
- Not applicable
- Details on results:
- Based on the biodegradation potential of the substance, it's more relevant to consider the result including biotransformation rate estimates instead of the result assuming a biotransformation rate of zero.
- Reported statistics:
- Not applicable
- Validity criteria fulfilled:
- yes
- Conclusions:
- The worst case Arnot-Gobas BCF for the substance is estimated at 334.6 L/Kg wet-wt (log BCF = 2.524), for the lower trophic, including biotransformation rate estimates.
- Executive summary:
The bioconcentration factor (BCF) of the substance was evaluated with the most recent model from BCFBAF model v3.01 from EPI Suite v4.1, which fulfilled all OECD principles. The substance is within the domain of the BCFBAF model based on the fragments present in the BCFBAF database.
Based on the biodegradation potential of the substance, it's more relevant to consider the result obtain with Arnot-Gobas Method, including biotransformation rate estimates instead of the result assuming a biotransformation rate of zero. The worst case Arnot-Gobas BCF for the substance is estimated at 334.6 L/Kg wet-wt (log BCF = 2.524), for the lower trophic, including biotransformation rate estimates.
Reference
Arnot-Gobas BCF model (Whole body Primary Biotransformation Rate estimate for fish):
TYPE |
NUM |
LOG BIOTRANSFORMATION FRAGMENT DESCRIPTION |
COEFF |
VALUE |
Frag Frag Frag Frag Frag L Kow MolWt Const |
1 1 4 4 2 * * * |
Ester [-C(=O)-O-C] Carbon with 4 single bonds & no hydrogens Methyl [-CH3] -CH2- [cyclic] -CH- [cyclic] Log Kow = 4.80 (user-entered) Molecular Weight Parameter Equation Constant |
-0.7605 -0.2984 0.2451 0.0963 0.0126 0.3073 |
-0.7605 -0.2984 0.9804 0.3850 0.0252 1.4752 -0.5085 -1.5058 |
RESULT RESULT NOTE |
Log Bio Half-life (days) Bio Half-life (days) Bio Half-life Normalized to 10 g fish at 15°C |
-0.2387 0.5772 |
Biotransformation rate constant:kM (rate constant) = 1.201 / day (10 gram fish).
Arnot-Gobas BCFBAF Methods (including biotransformation rate estimates):
Estimated Log BCF (upper trophic) = 2.369 (BCF = 234 L/Kg wet-wt).
Estimated Log BCF (mid trophic) = 2.490 (BCF = 309.2 L/Kg wet-wt).
Estimated Log BCF (lower trophic) = 2.524 (BCF = 334.6 L/Kg wet-wt).
Arnot-Gobas BCFBAF Methods (assuming a biotransformation rate of zero):
Estimated Log BCF (upper trophic) = 3.742 (BCF = 5515 L/Kg wet-wt).
Description of key information
Arnot-Gobas BCFBAF model v3.01 from EPI Suite v4.1, key data:
BCF = 334.6 L/kg whole body weight
Key value for chemical safety assessment
- BCF (aquatic species):
- 334.6 L/kg ww
Additional information
The key data point is not experimental but the bioconcentration factor (BCF) of the registered substance was evaluated with the most recent model from BCFBAF model v3.01 from EPI Suite v4.1, which fulfilled all OECD principles. The substance is within the domain of the Arnot-Gobas BCFBAF model based on the fragments present in the BCFBAF database.
Based on the biodegradation potential of the substance, it's more relevant to consider the result obtain with the Arnot-Gobas Method, including biotransformation rate estimates instead of the result assuming a biotransformation rate of zero. The BCF values of the substance are lower than 500 L/kg in all three general trophic levels of fish (lower, middle and upper). The worst case Arnot-Gobas BCF for the substance is estimated for the lower trophic level at 334.6 L/Kg wet-wt (log BCF = 2.524), including biotransformation rate estimates.
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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