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EC number: 807-747-9 | CAS number: 144429-84-5
- 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
Dermal absorption
Administrative data
- Endpoint:
- dermal absorption in vivo
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- guideline study
Cross-reference
- Reason / purpose for cross-reference:
- reference to same study
Data source
Reference
- Reference Type:
- study report
- Title:
- Unnamed
- Year:
- 2 006
Materials and methods
Test guideline
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 427 (Skin Absorption: In Vivo Method)
- Deviations:
- no
- GLP compliance:
- yes (incl. QA statement)
Test material
- Reference substance name:
- -
- EC Number:
- 406-040-9
- EC Name:
- -
- Cas Number:
- 125643-61-0
- Molecular formula:
- C24-26 H40-44 O3
- IUPAC Name:
- C7-9-(branched)-alkyl 3-(3,5-di-tert-butyl-4-hydroxyphenyl)propanoate
- Details on test material:
- Specific activity: 4.59 GBq/mmol; 124 mCi/mmol
Physical state: Liquid
Radiochemical purity: 96.0 - 99.8%
Solubility (20°C): Water: 0.5 +/- 0.7 µg/I; Methanol: >50 g/ml
The test material was stored below -15°C in the dark.
Non-radiolabelled test substance (supplied by Sponsor)
Purity: 98.8%
Storage: At ambient temperature in the dark.
Expiry date: 31 December 2010
Constituent 1
- Radiolabelling:
- yes
Test animals
- Species:
- mouse
- Strain:
- CD-1
- Sex:
- male
- Details on test animals or test system and environmental conditions:
- Strain as stated in the report: CD-l (albino) [Crl:CD1(ICR)]
Sex: Male
Bodyweight at dosing: 25 - 40 g
Age at dosing: 6-8 weeks
Supplier: Charles River UK Ltd., Margate, Kent, UK
Acclimatization: at least 5 days before the intended date of dosing.
Housing: During acclimatization animals were housed in groups of up to four mice in solid bottomed plastic cages.
After dosing, the animals were housed in sub-groups of 3 in glass metabolism cages (Metabowls®).
Diet ad libitum: VRFl diet manufactured by Special Diet Services
Water ad libitum: tap water
ENVIRONMENTAL CONDITIONS
Room temperature: 21 +/- 2°C.
Relative humidity: 55 - 15%.
Light/dark cycle: alternating 12 hour light/dark.
Air changes: approximately 15 per hour.
Administration / exposure
- Type of coverage:
- occlusive
- Vehicle:
- polyethylene glycol
- Duration of exposure:
- Animals were treated for 6 h.
- Doses:
- 0.5 mg/cm2, corresponding to 1mg/animal.
- No. of animals per group:
- 12 males
- Control animals:
- no
- Details on study design:
- RATIONALE FOR THE SELECTION OF THE DOSE ROUTE AND LEVEL
The dermal route was chosen as this is a expected route for human exposure to the test substance. Dose levels were selected upon worst case calculation for dermal exposure of worker.
DOSE PREPARATION AND PRUITY CHECK
14C-labeled test substance was stored in acetonitrile at a concentration of 495.91 µCi/mL (1.58 mg/mL) at or below -15°C. Dose formulations were freshly prepared on the day of administration.
The solvent of 3.2 mg 14C-labeled test substance-Stock solution (1005 µCi) was evaporated and the residue was re-suspended in PEG. Homogeneity of the formulation was kept by stirring at 50°C. Aliquots of the formulation were taken throughout the dosing procedure and pipette tips used for application were washed to accurately determine the applied dose. Purity checks of the dosing formulation were carried out and were >95%.
DETAILS ON EXPOSURE
24 h prior dosing the dorsal skin was clipped free of hair and cleaned with solvent. The dose formulation (0.025 mL) was applied to 2 cm2 of the dorsal skin of lightly anesthetized animals. The treated area was covered by foil and animals were allowed to recover from the anesthesia. The treated area was washed with cotton wool swabs soaked in 1% Tween 80 in distilled water 6 h after treatment. The application site was re-covered with foil to avoid oral exposure and subgroups of three mice were transferred to glass metabolism cages.
EXAMINATIONS
Urine was collected at time intervals of 0 - 6, 6 - 24 h, and subsequently at intervals of 24 h up to sacrifice after 168 hours into cooled receivers. Prior to dosing, pre-dose urine samples were collected for use as backgrounds.
Feces were collected separately into cooled receivers at 24 hour intervals up to 168 hours. Cage washes were performed every 24 h throughout the sample collection period and retained for radioactivity measurement.
Upon sacrifice the gastrointestinal tract (plus contents) was removed. The radioactivity of the carcass, gastrointestinal tract and feces was assessed after homogenization of the respective fraction.
In addition, the treated skin area was dissected and tape stripped to remove the stratum corneum. The initial first two tape strips were collected separately and represented the non-absorbed dose. Subsequent tape strips (3-8) containing the stratum corneum were retained and analyzed in groups of three. After tape stripping, the residual skin membranes and the tape strips were seperately solubilised until digestion was complete (7 days). The weight of the digest was measured and duplicate weighed aliquots were taken for radioassay.
The first 3 swabs used to remove non absorbed test substance after 6 h were pooled for each group of 3 mice and were extracted with methanol by sonication followed by centrifugation. The supernatant was decanted, weighed and duplicate samples were taken for radioassay. The above procedure was repeated twice more.
The protective dressings and foils were pooled for each group of 3 mice and extracted and analyzed as described above.
All samples not analyzed immediately after collection were placed into a freezer at <-15°C until analyzed.
Measurement of radioactivity
Radioactivity was measured by liquid scintillation counting (LSC) with automatic quench correction. Radioactivity below twice the background level was considered to be below the limit of detection. Aliquots of liquid samples were mixed with Ultima Gold scintillator (Packard BioScience) or Monoflow 4 for measurement of radioactivity.
Solid samples were combusted in oxygen using a sample oxidizer. The combustion products were absorbed into CO2 sorbent and mixed with Permafluor E+ scintillator. The efficiency of the oxidizer was found to be above than 95%. Measurements of radioactivity were corrected for oxidizer efficiency.
Results and discussion
- Total recovery:
- The overall mean recovery of radioactivity was 99.01% of the applied radioactivity. Mean tissue concentrations of radioactivity in carcass, gastrointestinal tract and treated skin corresponded to 2.26 %, 0.03 % and 0.07 % of applied dose.
Percutaneous absorption
- Key result
- Dose:
- 0.5 mg/cm2
- Parameter:
- percentage
- Absorption:
- 4.42 %
- Remarks on result:
- other: 6 h
- Remarks:
- The absorbable fraction of test substance was calculated as the sum of excreta, tissues, treated skin after stripping and stratum corneum in percent of applied radioactivity.
Any other information on results incl. tables
NON-ABSORBED RADIOACTIVITY
Following the topical application of 0.5 mg/cm2 14C-labeled test substance in PEG to mice under occlusive conditions, approximately 29% of the radioactivity applied was detected in the swabs used to clean the treated skin after 6 h. Another 65.4% of the applied radioactivity was extracted from the protective dressing.
The dose recovered from the treated skin (0.07%) and in the first two tape strips (0.27%) accounted for 0.34% of applied radioactivity. The mean total amount of non-absorbed (sum of the dose removed during the washing procedure and the dose remaining on the skin surface) accounted for 94.32% of applied radioactivity.
ABSORBED RADIOACTIVITY
Radioactivity detected in the stratum corneum corresponded to 0.26 % of the applied radioactivity. Radioactivity in urine, feces and cage washes accounted for 0.90%, 0.71% and 0.20% of applied radioactivity, respectively.
Radioactivity recovered in the gastrointestinal tract (including contents) accounted for 0.03% while 2.26% of applied radioactivity was detected in the carcass. The mean concentrations of radioactivity in carcass, treated skin, and gastrointestinal tract were 0.085, 0.021 and 0.006 µg equivalents/g wet weight, respectively.
The overall mean absorbable proportion of 14C-labelled test substance (sum of direct absorption [excreta, tissues], treated skin and stratum corneum) was 4.42% of applied radioactivity.
Table 1: Distribution of radioactivity detected after topical application of 14C-labelled test substance to male mice in percent of applied radioactive dose.
Sample |
Time point/interval (hours after dosing) |
||
6 h |
168 h |
0 - 168 h |
|
NON-ABSORBD DOSE |
|||
Swabs |
28.95 +/- 5.62 |
|
|
Dressing extracts |
59.62 +/- 5.60 |
5.75 +/- 2.17 |
|
Dose on surface (Strips1,2) |
|
0.27 +/-.0.09 |
|
TOTAL |
|
94.59 +/- 2.50 |
|
DIRECT ABSORPTION (Tissues & Excreta) |
|||
Urine total |
|
|
0.90 +/- 0.21 |
Feces total |
|
|
0.71 +/- 0.22 |
Carcass |
|
2.26 +/- 2.06 |
|
Gastrointestinal tract |
|
0.03 +/- 0.02 |
|
Cage wash |
|
0.20 +/- 0.03 |
|
TOTAL |
|
|
4.09 +/- 2.33 |
ABSORBABLE |
|||
Skin (after stripping) |
|
0.07 +/- 0.02 |
|
Stratum corneum |
|
0.26 +/- 0.16 |
|
TOTAL ABSORBABLE |
|||
Direct Absorption + treated skin + Stratum corneum |
|
|
4.42 +/- 2.40 |
OVERALL RECOVERY |
|||
Total |
|
|
99.01 +/- 1.95 |
Applicant's summary and conclusion
- Conclusions:
- After topical application of 14C-labeled test substance to male CD-1 mice according to OECD guideline 427, the mean total absorbed dose was 4.42 % of the applied radioactivity. Mean tissue concentrations of radioactivity in carcass, gastrointestinal tract and treated skin corresponded to 2.26%, 0.03% and 0.07% of applied dose.
The mean total non-absorbed dose was 94.59 % of the applied radioactivity. The mean overall recovery of radioactivity was 99.01% applied radioactivity.
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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