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EC number: 701-394-3 | CAS number: 1782069-81-1
- 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 vivo
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- study well documented, meets generally accepted scientific principles, acceptable for assessment
Data source
Reference
- Reference Type:
- publication
- Title:
- Kinetics of 3-(4-methylbenzylidene)camphor in rats and humans after dermal application
- Author:
- Schauer UMD, Völkel W, Heusener A, Colnot T, Broschard TH, von Landenberg F, Dekant W
- Year:
- 2 006
- Bibliographic source:
- Toxicology and Applied Pharmacology 216 (2006) 339–346
Materials and methods
- Objective of study:
- excretion
- metabolism
- toxicokinetics
Test guideline
- Qualifier:
- no guideline available
- Principles of method if other than guideline:
- - Principle of test: The toxicokinetics of 4-MBC after dermal administration were investigated in human subjects.
- Short description of test conditions: Humans (3 male and 3 female subjects) were exposed to 4-MBC by topical application of a commercial sunscreen formulation containing 4% 4-MBC (w/w), covering 90% of the body surface and resulting in a mean dermal 4-MBC dose of 22 mg/kg bw.
- Parameters analysed / observed: Concentrations of 4-MBC and its metabolites were monitored over 96 h in plasma and urine. - GLP compliance:
- not specified
- Remarks:
- Published study from a peer-reviewed journal.
Test material
- Reference substance name:
- (3E)-1,7,7-trimethyl-3-(4-methylbenzylidene)bicyclo[2.2.1]heptan-2-one
- EC Number:
- 701-394-3
- Cas Number:
- 1782069-81-1
- Molecular formula:
- C18H22O
- IUPAC Name:
- (3E)-1,7,7-trimethyl-3-(4-methylbenzylidene)bicyclo[2.2.1]heptan-2-one
Constituent 1
- Specific details on test material used for the study:
- Composition of formulation (w/w):
4.00% 4-methylbenzylidene camphor
2.00% glyceryl stearate, ceteareth-15
2.00% stearyl alcohol
1.00% microwax
1.00% butyrospermum parkii (shea butter)
6.00% C12-15 alkyl benzoate
6.00% caprylic/capric triglyceride
3.00% dibutyl adipate
0.50% dimethicone
1.00% glycerin
0.25% xanthan gum
73.25% aqua (water) - Radiolabelling:
- no
Test animals
- Species:
- other: human
- Details on species / strain selection:
- All subjects in the study had to refrain from alcoholic beverages and medicinal drugs 2 days before and throughout the experiment. Subjects did not abuse alcohol and were non-smokers. Subjects were healthy as judged by detailed medical anamnesis and had normal liver and kidney function based on clinical blood chemistry.
- Sex:
- male/female
- Details on test animals or test system and environmental conditions:
- The study was carried out according to the Declaration of Helsinki, after approval by the Regional Ethical Committee of the University of Würzburg, Germany, and after written informed consent by the subjects. Information on the test subjects is available in "Any other information on materials and methods incl. tables".
Administration / exposure
- Route of administration:
- dermal
- Vehicle:
- unchanged (no vehicle)
- Details on exposure:
- TEST SITE
- % coverage: 90% of body surface
REMOVAL OF TEST SUBSTANCE
- Washing: Subjects were permitted to take showers 12 h after application of the formulation. - Duration and frequency of treatment / exposure:
- Single application
Doses / concentrationsopen allclose all
- Dose / conc.:
- 20.76 mg/kg bw (total dose)
- Remarks:
- Subject A
- Dose / conc.:
- 21.41 mg/kg bw (total dose)
- Remarks:
- Subject B
- Dose / conc.:
- 20.41 mg/kg bw (total dose)
- Remarks:
- Subject C
- Dose / conc.:
- 23.58 mg/kg bw (total dose)
- Remarks:
- Subject D
- Dose / conc.:
- 21.88 mg/kg bw (total dose)
- Remarks:
- Subject E
- Dose / conc.:
- 24.16 mg/kg bw (total dose)
- Remarks:
- Subject F
- No. of animals per sex per dose / concentration:
- 3
- Control animals:
- no
- Positive control reference chemical:
- None used
- Details on study design:
- - Dose selection rationale: The application was intended to simulate a maximum exposure to 4-MBC.
- Details on dosing and sampling:
- TOXICOKINETIC / PHARMACOKINETIC STUDY (Absorption, distribution, excretion)
- Tissues and body fluids sampled: urine, blood, plasma
- Time and frequency of sampling: Plasma taken at 0, 0.5, 1, 2, 4, 6, 8, 12, 24, 36, 48, 60, 72, 84 and 96 h after application and urine taken in 8 h intervals.
METABOLITE CHARACTERISATION STUDIES
- Tissues and body fluids sampled: urine, plasma
- Time and frequency of sampling: Plasma taken at 0, 0.5, 1, 2, 4, 6, 8, 12, 24, 36, 48, 60, 72, 84 and 96 h after application and urine taken in 8 h intervals.
- From how many animals: 6
- Method type for identification: LC–MS/MS with electrospray ionisation.
- Limits of detection and quantification: Limit of detection for 4-MBC and its metabolites 3-(4-carboxybenzylidene)-6-hydroxycamphor and 3-(4-carboxybenzylidene)camphor in plasma and urine were between 1 and 20 pmol/mL.
- Other: 4-MBC metabolites 3-(4-carboxybenzylidene)-6-hydroxycamphor and 3-(4-carboxybenzylidene)camphor were isolated by preparative HPLC with UV detection.
TREATMENT FOR CLEAVAGE OF CONJUGATES: Human urine samples were pretreated with glucuronidase to cleave glucuronides before analysis. - Statistics:
- Standard deviations (mean ± SD), elimination half-lives and areas under the curve were calculated using Microsoft Excel. Polynoms given for best fit were transferred into “Functions” (Numerical-Mathematics.com) and AUCs were calculated from the mean of each time point.
Results and discussion
Toxicokinetic / pharmacokinetic studies
- Details on absorption:
- Peak plasma levels (Cmax) of 4-MBC were reached 6 h after dermal application. After the 6 h sampling point, 4-MBC concentrations decreased following 1st order kinetics to reach the limit of quantitation at 48 h (males) or 36 h (females) after the application. A precise number for the elimination half-lives could not be determined for the female participants due to insufficient data points for calculations, but are estimated to be similar to half-lives of male human subjects.
- Details on excretion:
- In urine samples, taken in 8 h intervals, concentrations of 4-MBC were below the limit of detection in all analysed samples.
Toxicokinetic parametersopen allclose all
- Key result
- Toxicokinetic parameters:
- Cmax: 200 pmol/mL
- Remarks:
- males
- Key result
- Toxicokinetic parameters:
- Cmax: 100 pmol/mL
- Remarks:
- females
- Key result
- Toxicokinetic parameters:
- half-life 1st: 9 hours
- Remarks:
- males
- Key result
- Toxicokinetic parameters:
- half-life 1st: 9 hours
- Remarks:
- females (estimated)
- Key result
- Toxicokinetic parameters:
- AUC: 3884 pmol/mL h
- Remarks:
- males
- Key result
- Toxicokinetic parameters:
- AUC: 1909 pmol/mL h
- Remarks:
- females
Metabolite characterisation studies
- Metabolites identified:
- yes
- Remarks:
- 3-(4-carboxybenzylidene)-6-hydroxycamphor; 3-(4-carboxybenzylidene)-6-hydroxycamphor glucuronide; 3-(4-carboxybenzylidene)camphor; 3-(4-carboxybenzylidene)-camphor glucuronide
- Details on metabolites:
- Peak concentrations of 3-(4-carboxybenzylidene)-6-hydroxycamphor and 3-(4-carboxybenzylidene)camphor in plasma were reached within 12 to 24 h after application. These concentrations were 50–80 pmol/mL for 3-(4-carboxybenzylidene)-6-hydroxycamphor and 100– 200 pmol/mL for 3-(4-carboxybenzylidene)camphor. Concentrations of 3-(4-carboxybenzylidene)-6-hydroxycamphor thereafter decreased with apparent half-lives of 31 h in males and 20 h in females. Apparent half-lives of elimination from plasma of 3-(4-carboxybenzylidene) camphor were calculated as 26 h in males and 23 h in females. AUC values in plasma were 2657 pmol/mL h for males and 1615 pmol/mL h for females for 3-(4-carboxybenzylidene)-6-hydroxycamphor and for 3-(4-darboxybenzylidene)camphor were 5782 pmol/mL h for males and 3029 pmol/mL h for females. Low, but quantifiable concentrations of both metabolites were still present in plasma 96 h after 4-MBC application. Estimated concentrations of a glucuronide of 3-(4-carboxybenzylidene)camphor in plasma were low (<5% of the concentration of 3-(4-carboxybenzylidene) camphor in 12 h blood samples).
Excretion in urine of both 3-(4-carboxybenzylidene)-6- hydroxycamphor and 3-(4-carboxybenzylidene)camphor (present as glucuronide) peaked within 16–24 h after dermal application. Without pretreatment with glucuronidase, the concentrations of 3-(4-carboxybenzylidene) camphor were very low in urine samples. With glucuronidase pretreatment, the concentrations of 3-(4-carboxybenzylidene)camphor were significantly increased, whereas only minor increases in the peak areas for 3-(4-carboxybenzylidene)-6-hydroxycamphor were seen. Both metabolites were still present in low concentrations in urine samples collected 96 h after 4-MBC application. Elimination half-lives for 3-(4-carboxybenzylidene)-6-hydroxycamphor were 26 h in males and 23 h in females and for 3-(4-carboxybenzylidene)camphor were 23 h in males and 18 h in females. AUC values in urine were 205203 nmol h for males and 123544 nmol h for females for 3-(4-carboxybenzylidene)-6-hydroxycamphor and for 3-(4-carboxybenzylidene)camphor were 49479 nmol h for males and 25268 nmol h for females. Less than 1% of the applied dose of 4-MBC was recovered in human urine as metabolites. For 3-(4-carboxybenzylidene)-6-hydroxycamphor, 0.4 ± 0.15% and 0.3 ± 0.01% of the applied 4-MBC dose was recovered in urine of males and females, respectively, and for 3-(4-carboxybenzylidene)camphor 0.10 ± 0.02% and 0.07 ± 0.02% of the applied 4-MBC dose was recovered in urine of males and females, respectively.
The molecular weight of the glucuronides of both 4-MBC metabolites are below 500 and thus below the threshold for biliary elimination in humans; therefore, elimination of 4-MBC metabolites with faeces in humans is considered unlikely.
Applicant's summary and conclusion
- Conclusions:
- Peak plasma levels (Cmax) of 4-MBC were reached 6 h after dermal application (200 pmol/ml in males and 100 pmol/ml in females). After the 6 h sampling point, 4-MBC concentrations decreased following 1st order kinetics with a half-life of 9 h to reach the limit of quantitation at 48 h (males) or 36 h (females) after the application. The AUC values were 3884 and 1909 pmol/mL h in males and females, respectively. In plasma, 3-(4-carboxybenzylidene)camphor is the major metabolic product, whereas, in urine, 3-(4-carboxybenzylidene)-6-hydroxycamphor and a glucuronide of 3-(4-carboxybenzylidene) camphor are major metabolites. Less than 1% of the applied dose of 4-MBC was recovered in urine as metabolites.
- Executive summary:
The toxicokinetics of 4-methylbenzylidene camphor after dermal administration were investigated in humans. Humans (3 male and 3 female subjects) were exposed to 4-MBC by topical application of a commercial sunscreen formulation containing 4% 4-MBC (w/w), covering 90% of the body surface and resulting in a mean dermal 4-MBC dose of 22 mg/kg bw. Concentrations of 4-MBC and its metabolites were monitored over 96 h in plasma and urine. Peak plasma levels (Cmax) of 4-MBC were reached 6 h after dermal application (200 pmol/ml in males and 100 pmol/ml in females). After the 6 h sampling point, 4-MBC concentrations decreased following 1st order kinetics with a half-life of 9 h to reach the limit of quantitation at 48 h (males) or 36 h (females) after the application. The AUC values were 3884 and 1909 pmol/mL h in males and females, respectively. In plasma, 3-(4-carboxybenzylidene)camphor is the major metabolic product, whereas, in urine, 3-(4-carboxybenzylidene)-6-hydroxycamphor and a glucuronide of 3-(4-carboxybenzylidene) camphor are major metabolites. Less than 1% of the applied dose of 4-MBC was recovered in urine as metabolites. This study is considered to be reliable with restrictions (Klimisch 2) as there are minor limitations in the reporting.
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