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Diss Factsheets
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EC number: 700-483-4 | CAS number: -
- 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:
- migrated information: read-across from supporting substance (structural analogue or surrogate)
- Adequacy of study:
- supporting study
- Study period:
- not reported; tables and plots dated 1984-04-19
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- other: no GLP study, but the test parameters documented are sufficient to accept the data (Klimisch et al., 1997)
Data source
Reference
- Reference Type:
- study report
- Title:
- Unnamed
- Year:
- 1 984
Materials and methods
Test guidelineopen allclose all
- Qualifier:
- equivalent or similar to guideline
- Guideline:
- OECD Guideline 427 (Skin Absorption: In Vivo Method)
- Version / remarks:
- (few similarities)
- Deviations:
- yes
- Qualifier:
- equivalent or similar to guideline
- Guideline:
- other: OECD Guideline 417 (Toxicokinetic)
- Deviations:
- yes
- Principles of method if other than guideline:
- No sufficient information about test substance, experimental animals, their housing and feeding conditions. One dose level of test substance was administered. No data on type of coverage of the applied area. No interpretation of results.
- GLP compliance:
- no
Test material
- Reference substance name:
- Diallyl 2,2'-oxydiethyl dicarbonate
- EC Number:
- 205-528-7
- EC Name:
- Diallyl 2,2'-oxydiethyl dicarbonate
- Cas Number:
- 142-22-3
- Molecular formula:
- C12H18O7
- IUPAC Name:
- diallyl 2,2'-oxydiethyl dicarbonate
- Details on test material:
- - Name of test material (as cited in study report): Carbon-14 labelled diallyl-diglycol carbonate (CR-39)
- Substance type: data not available
- Physical state: data not available
- Analytical purity: data not available
- Impurities (identity and concentrations): data not available
- Composition of test material, percentage of components: data not available
- Isomers composition: data not available
- Purity test date: data not available
- Lot/batch No.: 1222-145, assay number 81-221797
- Expiration date of the lot/batch: data not available
- Radiochemical purity (if radiolabelling): 1.29 microcuries
- Specific activity (if radiolabelling): data not available
- Locations of the label (if radiolabelling): (allyl-14C1) moiety of diallyl-diglycol carbonate
- Expiration date of radiochemical substance (if radiolabelling): data not available
- Stability under test conditions: data not available
- Storage condition of test material: data not available
- Other: The 14C labeled CR-39 utilized in this study was synthesized by New England Nuclear and was provided by the sponsor. A precipitant formed when the material was dissolved in absolute EtOH. The EtOH soluble fraction was assayed by thin layer chromatography using Silica Gel G. and a hexane:ether (40:60 , v/v) solvent system. The EtOH soluble fraction had the same rf value as a CR-39 reference standard. Only the EtOH soluble fraction was used in these studies.
Constituent 1
- Radiolabelling:
- yes
- Remarks:
- C14
Test animals
- Species:
- guinea pig
- Strain:
- not specified
- Sex:
- not specified
Administration / exposure
- Type of coverage:
- not specified
- Vehicle:
- ethanol
- Duration of exposure:
- 5 days
- Doses:
- - Nominal doses: 1.29 microcuries of C14 labeled CR-39
- Actual doses: no data
- Actual doses calculated as follows: no data
- Dose volume: 100 µL
- Rationale for dose selection: not reported - No. of animals per group:
- 3
- Control animals:
- no
Results and discussion
Percutaneous absorption
- Parameter:
- percentage
- Absorption:
- 0 %
- Remarks on result:
- other: 5 th day
- Remarks:
- excretion rates via urine and absorption % with and without washing were determined
- Conversion factor human vs. animal skin:
- not applicable
Any other information on results incl. tables
Remarks on tables and enclosed plots (see "Attached background material"):
Appendix 1 lists the parameters used in the subsequent data analysis.
Table number 1 lists the dpm values, the total volume of urine collected, and the calculated % dose excreted during each collection t ime interval for each subject. For example, under 0-6 hours for subject 1, 985.7 and 1013.3 are the calculated dpm values, 84 is the volume of urine collected in milliliters and 2.964 is the calculated % 14C dose excreted into the urine.
Table number 2 lists the % dose excreted into the urine and removed by the 24 hour washing procedure. The % dose excreted into the urine of CR-39 was determined to be 17.6% (standard deviation of 1.8). The maximum rate of excretion was observed during the first 24 hours. The 24 hour washing procedure removed 9.0% (standard deviation of 4.7) of the applied dose.
No 14C was detected in the feces, site of application or in the carcass of the animals.
Finally two graphs are enclosed. The first is a linear plot of the average % dose excreted into the urine per hour versus time at the midpoint of the collection period. The second is a semilog plot of the % dose excreted into the urine per hour versus time at the midpoint of the collection period.
Applicant's summary and conclusion
- Conclusions:
- The excretion rates were the highest within the first 24 hours. Percutaneous penetration of test substance is high.
17.6% of the applied dose were excreted into the urine during 5 days. The 24 hour washing procedure removed 9% (standard deviation) of the applied dose. No 14C was detected in the feces, site of application or in the carcass of animals. - Executive summary:
Carbon-14 labeled diallyl-diglycol carbonate (CR-39) was applied to the postauricular skin of the guinea pigs. Percutaneous absorption of the CR-39 was determined by measurement of the total amount of 14C label excreted into the urine.
The urine samples were collected every six hours the first day then daily for 5 days and assayed by liquid scintillation method. The skin of the animals was washed after 24 hours of application. The site of application and the remaining carcass were tested for C14 label.
17.6% of the applied dose were excreted into the urine during 5 days. The 24 hour washing procedure removed 9% (standard deviation) of the applied dose. No 14C was detected in the feces, site of application or in the carcass of animals.
Since the multi-constituent to be registered (EC 700-483-4) contains as main ingredient 'diallyl 2,2'oxydiethyl dicarbonate', the experimental data from this substance were used in a read-across approach.
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