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EC number: 228-250-8 | CAS number: 6197-30-4
- 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
Basic toxicokinetics
Administrative data
- Endpoint:
- basic toxicokinetics in vitro / ex vivo
- Type of information:
- experimental study
- Adequacy of study:
- other information
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- test procedure in accordance with generally accepted scientific standards and described in sufficient detail
Data source
Reference
- Reference Type:
- study report
- Title:
- Unnamed
- Year:
- 2 013
- Report date:
- 2013
Materials and methods
Test guideline
- Qualifier:
- no guideline followed
- Principles of method if other than guideline:
- The objective of this study was to investigate the hydrolytic stability of octocrilene in liver and gastrointestinal tract.
- GLP compliance:
- yes
- Remarks:
- In accordance with the OECD Principles of GLP with limitations: The protocol, the conduct of study and the "Summary of Results" of this study were not inspected by the QAU. This study does not have a GLP status.
Test material
- Reference substance name:
- Octocrilene
- EC Number:
- 228-250-8
- EC Name:
- Octocrilene
- Cas Number:
- 6197-30-4
- Molecular formula:
- C24H27NO2
- IUPAC Name:
- 2-ethylhexyl 2-cyano-3,3-diphenylacrylate
Constituent 1
- Radiolabelling:
- no
Administration / exposure
- Positive control reference chemical:
- Testosterone (200 μM) for rat liver S9 fraction
Benzyl benzoate (250 μM) for intestinal-fluid and gastric juice simulant. - Details on study design:
- Test substance was incubated in replicates at nominal concentrations of 100 and 250 μM for 2 h at 37°C with S9 fraction from rat liver, intestinal-fluid simulant including porcine pancreas lipase and gastric juice simulant. After incubation, the amount of remaining substrate was analysed in the appropriate incubate by HPLC/UV.
Negative Controls:
- Heat deactivated controls (HDC)
- Controls, directly stopped after addition of test substance (t=0 control) s
- Buffer control (BC, test substance in the incubation buffer) was used for calculation of recoveries in the HDC and t=0 controls.
Results and discussion
Metabolite characterisation studies
- Metabolites identified:
- yes
- Details on metabolites:
- In S9 fraction from rat liver: One metabolite (not further specified) could be detected that was more polar than octocrilene and was present in the active incubate but not in the performed control incubations.
This metabolite was not detected in the intestinal fluid and gastric juice in vitro system.
Any other information on results incl. tables
S9 fraction rat liver:
In the active incubate, it could be clearly demonstrated that octocrilene was metabolized under the applied incubation conditions. The mean metabolic turnover values were 70% (100μM) and 42% (250μM).
Recoveries of octocrilene (peak areas in HDC and t=0 control versus BC) were between 53-100% (100μM) and 82-98% (250μM).
Intestinal-fluid simulant:
Octocrilene was not metabolized in any of the active incubates as compared to controls. The mean metabolic turnover values were 1% (100μM) and 0% (250μM).
Recoveries were 52-65% (100μM) and 49- 54% (250μM). The relatively low recoveries are assumed to be based on the lipophilicity of the test substance that may bind to the surface of the reaction vessels.
Gastric juice simulant:
Lower peak areas (as compared to t=0 controls) were observed in the active incubates for octocrilene. The mean metabolic turnover values were 0% (100μM) and 19.5% (250μM). Although this finding may imply that octocrilene was partly hydrolyzed by gastric juice simulant this interpretation is questionable since the polar metabolite observed in incubates of liver S9 fraction, being attributed to the degradation product of the substrate was not detected in this in vitro system.
Positive controls
Testosterone was metabolized extensively in liver S9 fraction (100% metabolic turnover).
Benzyl benzoate was hydrolyzed completely in intestine fluid simulant (100% metabolic turnover). In gastric juice simulant lower peak areas as compared to t=0 controls were observed in the active incubates (i.e. 57% metabolic turnover) and demonstrated that the positive control Benzyl benzoate partly degraded in this in vitro system.
In vitro system |
Concentration [µM] |
Replicate |
Recovery (HDC/BC*100) [%] |
Recovery (t=0/BC*100) [%] |
Metabolic turnover [%] |
Liver S9 fraction |
100 | 1 | 97.1 | 100.4 | 77.6 |
2 | 60.1 | 52.8 | 63.1 | ||
250 | 1 | 82.4 | 98.4 | 22.6 | |
2 | 83.6 | 90.6 | 62.3 | ||
Intestinal fluid simulant |
100 | 1 | 55.9 | 65.0 | 0.0 |
2 | 52.0 | 54.1 | 2.0 | ||
250 | 1 | 52.0 | 54.1 | 0.0 | |
2 | 49.3 | 49.9 | 0.0 | ||
Gatric fluid simulant |
100 | 1 | - | - | 0.0 |
2 | - | - | 0.0 | ||
250 | 1 | - | - | 34.3 | |
2 | - | - | 4.8 |
Applicant's summary and conclusion
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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