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EC number: 207-355-2 | CAS number: 464-49-3
- 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
Developmental toxicity / teratogenicity
Administrative data
- Endpoint:
- developmental toxicity
- Type of information:
- experimental study
- Adequacy of study:
- weight of evidence
- Reliability:
- 1 (reliable without restriction)
Data source
Reference
- Reference Type:
- review article or handbook
- Title:
- Unnamed
- Year:
- 1 992
Materials and methods
Test guideline
- Qualifier:
- according to guideline
- Guideline:
- other: the Food and Drug Administration (FDA) Good Laboratory Practice Regulations for Nonclinical Studies (GLP Guidelines) (FDA, 1988)
- GLP compliance:
- yes
Test material
- Reference substance name:
- (+)-bornan-2-one
- EC Number:
- 207-355-2
- EC Name:
- (+)-bornan-2-one
- Cas Number:
- 464-49-3
- Molecular formula:
- C10H16O
- IUPAC Name:
- 1,7,7-trimethylbicyclo[2.2.1]heptan-2-one
Constituent 1
Test animals
- Species:
- rabbit
- Strain:
- New Zealand White
- Details on test animals or test system and environmental conditions:
- during the study, lights were on from 0700h to 1900h. the ranges of average temperature and humidity for these two rooms within each replicate were 65-66 ℉ and 58%-64%, respectively
Administration / exposure
- Route of administration:
- oral: gavage
- Vehicle:
- corn oil
- Details on analytical verification of doses or concentrations:
- Dose Selection. The dose levels selected for this study were based on
preliminary data furnished by the sponsor (NTP. 1990). The NTP preliminary
study found that doses of 1.250 or 2.500 mg/kg/day d-Camphor given by gavage
were highly toxic. Only one of the ten dams in the 2.500 mg/kg/day group
survived past gd 7. and it had to be euthanized on gd 10. Of the ten dams in the 1.250 mg/kg/day group. only one survived the 10-day treatment: the rest of
the dams either died or were sacrificed moribund on or before gd 10. Ataxia
and lethargy were common in these two groups and convulsions were occasionally
observed. Of the other doses tested (100. 500. and 800 mg/kg/day). only the
800_mg/kg/day dose produced any maternal or fetal toxicity. - Frequency of treatment:
- Animals were observed daily before (gd 0-5). during (gd6-19). and after (gd 20-30) dosing for clinical signs of toxicity
Doses / concentrationsopen allclose all
- Dose / conc.:
- 100 mg/kg bw/day (nominal)
- Remarks:
- camphor
- Dose / conc.:
- 400 mg/kg bw/day (nominal)
- Remarks:
- camphor
- Dose / conc.:
- 800 mg/kg bw/day (nominal)
- Remarks:
- camphor
- No. of animals per sex per dose:
- n-13-16 females per group per replicate
Examinations
- Maternal examinations:
- There were no CAM-related maternal deaths during the study, but two does were removed from the 400 mg/kg/day CAM group because of dosing errors.
Maternal weight gain relative to control does was reduced 13%. 5%. and 59% in the 50, 200. and 400 mg/kg/day CAM groups. respectively. Gravid uterine and absolute and relative maternal liver weights were similar to vehicle control values. - Statistics:
- General Linear Models (GLM) procedures were applied for the analyses of variance (ANOVA) of maternal and fetal parameters (SAS Institute. 1989a.b: 1990a.b.c)
Nominal scale measures were analyzed by a x2 test for independence and by a test for linear trend on proportions. When a X2 test showed significant group differences. a onetailed Fisher's exact probability test was used for pair~ise comparisons of CAM and control groups.
Results and discussion
Results: maternal animals
General toxicity (maternal animals)
- Food consumption and compound intake (if feeding study):
- effects observed, treatment-related
- Description (incidence and severity):
- Food intake was significantly
decreased in the 400 (12%) and 800 (21%) mg/kg/day groups on gd 6 to 9. but
returned to control levels in both groups by gd 9 to 12. There was no
significant effect of 100 mg/kg/day CAM on maternal food consumption - Water consumption and compound intake (if drinking water study):
- effects observed, treatment-related
- Description (incidence and severity):
- Relative water intake
in the two groups went from 115% of controls on gd 6 to 9 to 130-136% at the
end of the dosing period. Water consumption in these groups remained 18·32%
above controls through gd 18 to 20. Smaller increases in relative maternal
water intake were noted for 100 mg/kg/day CAM. but a significant effect was
observed only on gd 6 to 9 - Behaviour (functional findings):
- effects observed, treatment-related
- Description (incidence and severity):
- The incidence of hypoactivity/lethargy in the 800 mg/kg/day group fell from 27% (7/26) on gd 6. to 8% (2/26) on gd 7. and finally to 0% on
gd 8. - Details on results:
- Both 400 and 800 mg/kg/day CAM produced comparable and consistent
increases in maternal water intake (Figure 4; Table 1). Relative water intake
in the two groups went from 115% of controls on gd 6 to 9 to 130-136% at the
end of the dosing period. Water consumption in these groups remained 18·32%
above controls through gd 18 to 20. Smaller increases in relative maternal
water intake were noted for 100 mg/kg/day CAM. but a significant effect was
observed only on gd 6 to 9. Dose-dependent effects of CAM on maternal food
consumption were also seen. but they were transient and opposite those seen
for water consumption (Figure 3: Table 1). Food intake was significantly
decreased in the 400 (12%) and 800 (21%) mg/kg/day groups on gd 6 to 9. but
returned to control levels in both groups by gd 9 to 12. There was no
significant effect of 100 mg/kg/day CAM on maternal food consumption.
Clinical signs of maternal toxicity were infrequent and generally
confined to the 800 mg/kg/day group. In that group. the most commonly
observed clinical sign was hypoact;vity. which was confined to the first two
days of dosing. The incidence of hypoactivity/lethargy in the 800 mg/kg/day group fell from 27% (7/26) on gd 6. to 8% (2/26) on gd 7. and finally to 0% on
gd 8. The above results indicate that the maternal lowest-observed-adverseeffect
level (LOAEL) for CAM-induced maternal toxicity was ~ 100 mg/kg.
although the magnitude of the effects at this dose was small.
Effect levels (maternal animals)
- Dose descriptor:
- LOAEL
- Effect level:
- < 100 mg/kg bw/day
- Based on:
- test mat.
- Basis for effect level:
- other: maternal toxicity
Results (fetuses)
- Fetal body weight changes:
- no effects observed
- Changes in litter size and weights:
- no effects observed
- External malformations:
- no effects observed
- Skeletal malformations:
- no effects observed
- Visceral malformations:
- no effects observed
- Details on embryotoxic / teratogenic effects:
- Embryotoxic / teratogenic effects:no effects
Details on embryotoxic / teratogenic effects:
The results from this study indicate that 400 mg/kg/day CAM administered orally to pregnant New Zealand White rabbits on gd 6-19 is not developmentally
toxic. These results are consistent with those found after the oral administration of CAM in (Sprague-Dawley) rats on gd 6-15 (NTP. 1991). In that study. doses of 400 mg/kg/day or 800 mg/kg/day CAM had no adverse effect on fetal growth. viability. or morphological development. However. CAM did cause minor maternal toxicity inJthe form of decreased maternal weight gain and altered food and water consumption in rats.
Effect levels (fetuses)
- Dose descriptor:
- NOAEL
- Effect level:
- > 800 mg/kg bw/day (nominal)
- Based on:
- test mat.
- Sex:
- not specified
- Basis for effect level:
- external malformations
- skeletal malformations
- visceral malformations
Fetal abnormalities
- Abnormalities:
- not specified
Overall developmental toxicity
- Developmental effects observed:
- not specified
Any other information on results incl. tables
Embryo/fetal development was unaffected by CAM
administration. Results of the uterine examination revealed that the number
of corpora lutea per dam and the number of implantation sites per litter in
the CAM-treated dams were within 99-107% of control values (Table 2). The
number of live fetuses per litter and the average fetal body weight were
likewise unaffected (Table 2).
Applicant's summary and conclusion
- Conclusions:
- The results from this study indicate that CAM is neither developmentally toxic nor toxic to the does at doses as high as 400 mg/kg/day
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