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EC number: 701-188-3 | 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
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- Nanomaterial pour density
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- 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:
- key study
- Study period:
- From 08 November 2013 to 14 January 2014
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- guideline study
- Remarks:
- GLP study conducted according to OECD Guideline 414 without deviation.
Cross-referenceopen allclose all
- Reason / purpose for cross-reference:
- reference to other study
- Reason / purpose for cross-reference:
- reference to same study
Data source
Reference
- Reference Type:
- other: audited draft report
- Title:
- Unnamed
- Year:
- 2 014
Materials and methods
Test guideline
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 414 (Prenatal Developmental Toxicity Study)
- Deviations:
- no
- Principles of method if other than guideline:
- Not applicable
- GLP compliance:
- yes (incl. QA statement)
- Limit test:
- no
Test material
- Reference substance name:
- (R)-α,α,4-trimethylcyclohex-3-ene-1-methanol
- EC Number:
- 232-081-5
- EC Name:
- (R)-α,α,4-trimethylcyclohex-3-ene-1-methanol
- Cas Number:
- 7785-53-7
- Molecular formula:
- C10H18O
- IUPAC Name:
- α,α-4-trimethyl-(1R)-3-cyclohexene-1-methanol
- Reference substance name:
- p-menth-1-en-8-ol
- EC Number:
- 233-986-8
- EC Name:
- p-menth-1-en-8-ol
- Cas Number:
- 10482-56-1
- Molecular formula:
- C10H18O
- IUPAC Name:
- α,α-4-trimethyl-(1S)-3-cyclohexene-1-methanol
- Reference substance name:
- 1-methyl-4-(1-methylethylidene)cyclohexan-1-ol
- EC Number:
- 209-584-3
- EC Name:
- 1-methyl-4-(1-methylethylidene)cyclohexan-1-ol
- Cas Number:
- 586-81-2
- Molecular formula:
- C10H18O
- IUPAC Name:
- 1-methyl-4-(1-methylethylidene)-cyclohexanol
- Reference substance name:
- cis-4-isopropenyl-1-methylcyclohexanol
- Cas Number:
- 7299-41-4
- Molecular formula:
- C10H18O
- IUPAC Name:
- cis-4-isopropenyl-1-methylcyclohexanol
- Reference substance name:
- trans-1-methyl-4-(1-methylethenyl)-cyclohexanol
- Cas Number:
- 7299-40-3
- Molecular formula:
- C10H18O
- IUPAC Name:
- trans-1-methyl-4-(1-methylethenyl)-cyclohexanol
- Reference substance name:
- 4-(isopropyl)-1-methylcyclohex-3-en-1-ol
- EC Number:
- 209-585-9
- EC Name:
- 4-(isopropyl)-1-methylcyclohex-3-en-1-ol
- Cas Number:
- 586-82-3
- Molecular formula:
- C10H18O
- IUPAC Name:
- 4-isopropyl-1-methyl-3-cyclohexen-1-ol
- Test material form:
- liquid
- Details on test material:
- Batch No.: 148465
Purity: 82.9% (sum of the three main constituents)
Name of test material (as cited in study report): TERPINEOL MULTICONSTITUENT
Physical state: colourless liquid
Storage conditions: +2°C to +8°C, under nitrogen and protected from light
Expiry date: 09 September 2013
Constituent 1
Constituent 2
Constituent 3
impurity 1
impurity 2
impurity 3
Test animals
- Species:
- rat
- Strain:
- Sprague-Dawley
- Details on test animals or test system and environmental conditions:
- TEST ANIMALS
- Source: Charles River (UK) Ltd.
- Number of animals ordered: 88 females; spare animals were removed from the study room after treatment commenced.
- Age of the animals at the start of the study (day 0 of gestation): at least 70 days old.
- Weight range of the animals at the start of the study (day 0 of gestation): 235 to 286 g.
HOUSING
- Cages: cages comprised of a polycarbonate body with a stainless steel mesh lid; changed at appropriate intervals. Solid (polycarbonate) bottom cages were used during the acclimatisation and gestation periods. Grid bottomed cages were used during pairing. Cages were suspended above absorbent paper which was changed daily during pairing.
- Number of animals per cage during acclimatisation up to four animals; during pairing one (stud) male and one female; during gestation: one female.
- Diet: ad libitum. SDS VRF1 certified pelleted diet. The diet contained no added antibiotic or other chemotherapeutic or prophylactic agent.
- Water: potable water from the public supply via polycarbonate bottles with sipper tubes. Bottles were changed at appropriate intervals. Ad libitum.
- Duration of acclimatisation: five days before commencement of pairing.
ENVIRONMENTAL CONDITIONS
- Temperature: 19-23ºC.
- Humidity: 40-70%.
- Air changes: approximately 15 to 20 per hour.
- Air supply: filtered fresh air which was passed to atmosphere and not recirculated.
- Photoperiod (artificial lighting): 12 h dark / 12 h light
- rodent facility: full barrier - to minimise entry of external biological and chemical agents and to minimise the transference of such agents between rooms.
Administration / exposure
- Route of administration:
- oral: gavage
- Vehicle:
- corn oil
- Details on exposure:
- METHOD OF PREPARATION
Vehicle was gradually added to the required amount of test substance and mixed to produce a pourable suspension. The suspension was quantitatively transferred and diluted to volume and finally mixed using a high-shear homogeniser. A series of suspensions at the required concentrations were prepared by dilution of individual weighings of the test substance.
The use of plastic or rubber equipment/storage containers was avoided.
VEHICLE
- Concentration in vehicle: determined for each formulation.
- Amount of vehicle (if gavage): 5 mL/kg body weight.
- Justification for use and choice of vehicle (if other than water): substance only slightly soluble in water.
- Formulation frequency: weekly and prepared in advance of the first day of use. The homogeneity and stability of formulations in the concentration range 1 to 200 mg/mL were confirmed for 15 days following refrigerated storage (2-8˚C) and for 2 days following ambient storage (nominally 21˚C) as part of another study, Huntingdon Life Sciences (OAD0004). - Analytical verification of doses or concentrations:
- yes
- Details on analytical verification of doses or concentrations:
- Concentration in test formulations:
- Verification: on Day 1 of dosing and the last day of dosing, freshly prepared test formulations were sampled (4 × 1 mL accurately weighed, 2 × 3 mL accurately weighed for controls) and submitted for analysis. Duplicate samples were analysed in accordance with the analytical procedure, and the remaining samples were retained for contingency. These were discarded following acceptable results.
- Results: the mean concentrations of Terpineol multiconstituent in test formulations analysed for the study were within 4% of nominal concentrations, confirming accurate formulation.
Analytical procedure:
The analytical method involved extraction and dilution in acetone followed by gas chromatography analysis with flame ionisation detection. Sample concentrations were determined with reference to external standards prepared in the concentration range 5 μg/mL to 25 μg/mL. - Details on mating procedure:
- - Male/female ratio per cage: 1:1 with identified stock males.
- Daily checks for evidence of mating: Ejected copulation plugs in cage tray and vaginal smears were checked for the presence of sperm.
- Day 0 of gestation: When positive evidence of mating was detected.
- Further matings after two unsuccessful attempts: no data
- Verification of same strain and source of both sexes: no data
- Allocation: On the day of positive evidence of mating (Day 0). Only females showing at least two copulation plugs were allocated.
A colony of stud males was maintained specifically for the purpose of mating; these animals were not part of the study and were maintained as stock animals. - Duration of treatment / exposure:
- Day 6 to 19 after mating, inclusive.
- Frequency of treatment:
- Females were treated from Day 6 to Day 19 (inclusive) after mating, once daily at approximately the same time each day.
- Duration of test:
- 21 days (Days 0-20 post coitum)
- No. of animals per sex per dose:
- 20 mated females/dose
- Control animals:
- yes, concurrent vehicle
- Details on study design:
- - Dose selection rationale: The dose levels of 60, 200 and 600 mg/kg bw/day were selected in agreement with the Sponsor.
- Volume dose: 5 mL/kg body weight.
- Rationale for animal assignment, method: To group and cage position in the sequence of mating. Females mating on any one day were evenly distributed amongst the groups. Allocation was controlled to prevent any stock male from providing more than one mated female in each treatment group.
- Identification of animals: Each animal was assigned a number and identified uniquely within the study by a tail tattoo.
- Identification of cages: Each cage label was colour-coded according to group and was numbered uniquely with cage and study number, as well as the identity of the occupant(s).
Examinations
- Maternal examinations:
- CAGE SIDE & CLINICAL OBSERVATIONS: Yes
Time schedule:
- Mortality or signs of morbidity: Animals were inspected visually at least twice daily for evidence of ill-health or reaction to treatment. Cages and cage-trays were inspected daily for evidence of animal ill-health amongst the occupant(s). Any deviation from normal was recorded at the time in respect of nature and severity, date and time of onset, duration and progress of the observed condition, as appropriate. During the acclimatisation period, observations of the animals and their cages were recorded at least once per day.
- Clinical signs: A detailed physical examination was performed on each animal on Days 0, 5, 12, 18 and 20 after mating to monitor general health.
BODY WEIGHT: Yes
- Time schedule for examinations: the weight of each adult was recorded on Days 0, 3 and then daily from Days 6 to 20 after mating.
FOOD CONSUMPTION AND COMPOUND INTAKE (if feeding study): Yes
- Time schedule: The weight of food supplied to each adult, that remaining and an estimate of any spilled was recorded for the periods Days 0-2, 3-5, 6-9, 10-13, 14-17 and 18-19 inclusive after mating.
POST-MORTEM EXAMINATIONS: Yes
- Time schedule: animals were killed on Day 20 after mating
OTHER:
Preservation of tissues: All adult animals were subject to a detailed necropsy. After a review of the history of each animal, a full macroscopic examination of the tissues was performed - Ovaries and uterine content:
- The ovaries and uterine content was examined after termination: Yes
Examinations included:
- Gravid uterus weight: Yes (including cervix and ovaries), for pregnant females surviving to term
- Number of corpora lutea: Yes, for all females
- Number of implantations: Yes, for all females
- Number of early resorptions: Yes, for all females
- Number of late resorptions: Yes, for all females
- Other: fetuses (live and dead), for all females
- For apparently empty uterine horns: The number of uterine implantation sites were checked after staining with ammonium sulphide - Fetal examinations:
- EXAMINATION OF FETUSES:
- Number of all live fetuses: Yes
- Number of dead fetuses (fetuses at term without spontaneous movements and breathing): Yes
- Fetuses eviscerated were fixed in Industrial Methylated Spirit (IMS). Remaining fetuses were fixed whole in Bouin’s fluid.
- Body weight of fetuses: Body weight of each live fetus was recorded.
- Sex of fetuses: Sex of each fetus was determined.
- External examinations: Yes; each fetus was subjected to a detailed external examination, which included the observation of all visible structures, surfaces and orifices.
- Soft tissue examinations: Yes, 50% of the live fetuses in each litter were sexed internally and eviscerated.
- Skeletal examinations: Yes [all the remaining litters].
- Head examinations: Yes, cleft lip, protruding tongue, craniorachischisis, open eye lid(s), short snout,
- Skin examination: shinny, subcutaneous oedema - Statistics:
- - The computer systems that were used on this study to acquire and quantify data include: Liberate, in-house system used for reporting in-life, necropsy, fetal pathology and statistics.
- Pre/post implantation loss and sex ratio were analysed by generalised mixed linear model with binomial errors, a logit link function and litter as a random effect
- Each treated group was compared to control using a Wald chi-square test.
- For resorptions, each treated group was compared to control by exact Wilcoxon rank sum test
- The mean values: group mean values and SD were calculated using individual litter mean values. - Indices:
- - Pre-implantation loss (%): [(Number of corpora lutea - Number of implantations) / Number of corpora lutea] X 100
- Post-implantation loss (%): [(Number of implantations - Number of live fetuses) / Number of implantations] X 100
- Sex ratios of the foetuses were calculated as the percentage of males per litter.
- All group values and SD (as appropriate) were calculated from the individual litter values.
- For litter size and survival indices and fetal, placental and litter weight and gravid uterine weight data, if 75% of the data (across all groups) were the same value, for example c, Fisher’s Exact tests were performed. - Historical control data:
- The results of 8 groups corresponding to historical control data are presented in Annex 3 of the report.
We can find the number of fetuses/litters examined, the number of incompletely ossified/unossified skeletals (5th/6th sternebrae, other sternebrae, total number of affected fetuses/litters, mean % fetuses per litter with affected sternebrae).
Results and discussion
Results: maternal animals
General toxicity (maternal animals)
- Clinical signs:
- no effects observed
- Description (incidence and severity):
- Signs in relation to dose administration were limited to a low incidence of salivation or chin rubbing among females receiving 600 mg/kg/day.
- Mortality:
- no mortality observed
- Description (incidence):
- No mortality and no relevant clinical signs or signs of reaction to treatment were noted in treated females.
- Body weight and weight changes:
- effects observed, treatment-related
- Description (incidence and severity):
- -Following the commencement of treatment on Day 6 of gestation, females in the 600 mg/kg/day group showed statistically significantly low mean body weight gain compared to Controls between Day 6 and 8 of gestation (3g versus 6g among Controls). A similar statistically significant decrease in mean body weight gain was evident among these females between Day 12 and Day 15 of gestation (17g versus 21g among Control), and mean weight gain from Day 15 to Day 20 of gestation was 0.93X Control although statistical significance was not attained for this difference. As a consequence, overall mean weight gain from Day 6 to Day 20 of gestation for females receiving 600 mg/kg/day was statistically significantly lower than Control (0.92X Control). There was no effect of treatment with Terpineol on the weight gain of females receiving 60 or 200 mg/kg/day.
- Food consumption and compound intake (if feeding study):
- effects observed, treatment-related
- Description (incidence and severity):
- Following the commencement of treatment on Day 6 of gestation, mean food intake among females in the 600 mg/kg/day group was slightly lower than Control throughout the treatment period, with statistical significance attained for the differences during Days 6-17 of gestation. Mean food intake for females in the 60 or 200 mg/kg/day groups was unaffected by treatment with Terpineol.
- Food efficiency:
- not examined
- Ophthalmological findings:
- not examined
- Haematological findings:
- not examined
- Clinical biochemistry findings:
- not examined
- Urinalysis findings:
- not examined
- Behaviour (functional findings):
- not examined
- Immunological findings:
- not examined
- Organ weight findings including organ / body weight ratios:
- effects observed, treatment-related
- Description (incidence and severity):
- At scheduled termination on Day 20 of gestation, the mean gravid uterine weight of females in the 600 mg/kg/day group was slightly lower than Control (0.94X) and when overall mean body weight gain was adjusted for the contribution of the gravid uterus, net body weight gain during gestation was also lower than Control (0.85X); these differences from Control did not, however, attain statistical significance. Mean gravid uterine weight and net mean body weight gain were similar to Control for females receiving 60 or 200 mg/kg/day and no effect of treatment was inferred.
- Gross pathological findings:
- no effects observed
- Description (incidence and severity):
- - There were no treatment-related macroscopic abnormalities detected at scheduled termination at any dose level investigated.
- Two females in the 200 mg/kg/day group (No’s. 47 and 49) were noted to have a misshapen liver with a raised area protruding through the diaphragm, resulting in a diaphragmatic hernia; these abnormalities were deemed to be congenital and unrelated to treatment with Terpineol. - Neuropathological findings:
- not examined
- Histopathological findings: non-neoplastic:
- not examined
- Histopathological findings: neoplastic:
- not examined
- Other effects:
- not examined
Maternal developmental toxicity
- Number of abortions:
- no effects observed
- Pre- and post-implantation loss:
- no effects observed
- Total litter losses by resorption:
- effects observed, non-treatment-related
- Description (incidence and severity):
- - With the exception of one female in the 200 mg/kg/day group (No. 52) which had a total litter resorption, all females were found to be pregnant with live young at scheduled termination on Day 20 of gestation.
- Early or late resorptions:
- no effects observed
- Dead fetuses:
- no effects observed
- Changes in pregnancy duration:
- no effects observed
- Description (incidence and severity):
- Migrated Data from removed field(s)
Field "Effects on pregnancy duration" (Path: ENDPOINT_STUDY_RECORD.DevelopmentalToxicityTeratogenicity.ResultsAndDiscussion.ResultsMaternalAnimals.MaternalDevelopmentalToxicity.EffectsOnPregnancyDuration): no effects observed - Changes in number of pregnant:
- no effects observed
- Other effects:
- not examined
Effect levels (maternal animals)
- Key result
- Dose descriptor:
- NOAEL
- Effect level:
- 600 mg/kg bw/day
- Based on:
- test mat.
- Basis for effect level:
- other: maternal toxicity
Maternal abnormalities
- Abnormalities:
- no effects observed
Results (fetuses)
- Fetal body weight changes:
- not specified
- Description (incidence and severity):
- Migrated Data from removed field(s)
Field "Fetal/pup body weight changes" (Path: ENDPOINT_STUDY_RECORD.DevelopmentalToxicityTeratogenicity.ResultsAndDiscussion.ResultsFetuses.FetalPupBodyWeightChanges): not examined - Reduction in number of live offspring:
- no effects observed
- Changes in sex ratio:
- no effects observed
- Changes in litter size and weights:
- effects observed, treatment-related
- Description (incidence and severity):
- At 600 mg/kg/day marginally low mean male and female fetal weight was apparent, with statistical significance attained for mean female fetal weight when compared to Control (0.95X), resulting in marginally but statistically significantly low overall mean fetal weight (0.96X Control). In addition, mean placental weight in this dose group was slightly low (0.91X Control) with differences attaining statistical significance. Mean placental, litter and fetal weights at 60 or 200 mg/kg/day were unaffected by maternal treatment with Terpineol.
- Changes in postnatal survival:
- not examined
- External malformations:
- no effects observed
- Description (incidence and severity):
- The incidence of major and minor abnormalities and skeletal variants showed no relationship to maternal treatment with Terpineol.
- Skeletal malformations:
- effects observed, non-treatment-related
- Description (incidence and severity):
- At 600 mg/kg/day there was a slightly higher incidence of incompletely ossified or unossified 5th and/or 6th sternebrae compared to concurrent control and the Historical Control Data range. In the absence of any related abnormalities this finding was considered to reflect a minor delay in development, indicated by the marginally decreased mean fetal body weight in this group, rather than a direct effect of treatment on fetal development.
- Visceral malformations:
- no effects observed
- Other effects:
- not examined
Effect levels (fetuses)
- Key result
- Dose descriptor:
- NOAEL
- Effect level:
- 600 mg/kg bw/day (actual dose received)
- Based on:
- test mat.
- Sex:
- male/female
- Basis for effect level:
- other: developmental toxicity
Fetal abnormalities
- Abnormalities:
- no effects observed
Overall developmental toxicity
- Developmental effects observed:
- no
Any other information on results incl. tables
Table 7.8.2/2: Clinical signs – group distribution of observations
Days 0 - 20 |
Number of animals affected |
||||||||||
Group / sex |
1F |
2F |
3F |
4F |
|||||||
Category |
Observations |
Number in group |
20 |
20 |
20 |
20 |
|||||
Coat |
Hair loss, forelimbs |
|
1 |
2 |
4 |
6 |
Table 7.8.2/3: Signs associated with dosing - group distribution of observations
Sign |
Day number |
Group/sex and number of animals showing sign |
|||||||
1F |
2F |
3F |
4F |
||||||
Behaviour |
|
||||||||
|
Chin Rubbing |
17 |
0 |
0 |
0 |
3 |
|||
|
|
18 |
0 |
0 |
0 |
7 |
|||
|
|
19 |
0 |
0 |
0 |
6 |
|||
Salivation |
7 |
0 |
0 |
0 |
3 |
||||
|
|
8 |
0 |
0 |
0 |
7 |
|||
|
|
11 |
0 |
0 |
0 |
1 |
|||
|
|
12 |
0 |
0 |
0 |
2 |
|||
|
|
13 |
0 |
0 |
0 |
2 |
|||
|
|
14 |
0 |
0 |
0 |
2 |
|||
|
|
15 |
0 |
0 |
0 |
1 |
Table 7.8.2/4: Food consumption - group mean values (g/animal/day) during gestation
|
|||||||||
|
|||||||||
Group/Sex |
|
Day 0-2 |
Day3-5 |
Day 6-9 |
Day 10-13 |
Day 14-17 |
Day 18-19 |
||
Statistical test |
|
Av |
Av |
Wi |
Wi |
Wi |
Wi |
||
1F |
Mean |
25 |
26 |
23 |
25 |
27 |
26 |
||
|
SD |
2.0 |
2.4 |
2.5 |
3.1 |
2.4 |
2.5 |
||
|
N |
20 |
20 |
20 |
20 |
20 |
20 |
||
2F |
Mean |
25 |
26 |
24 |
25 |
28 |
27 |
|
|
|
SD |
1.9 |
2.0 |
1.7 |
2.1 |
2.3 |
3.2 |
|
|
|
N |
20 |
20 |
20 |
20 |
20 |
20 |
|
|
3F |
Mean |
25 |
26 |
22 |
25 |
28 |
28 |
|
|
|
SD |
2.3 |
2.3 |
1.5 |
2.3 |
2.3 |
3.2 |
|
|
|
N |
19 |
19 |
19 |
19 |
19 |
19 |
|
|
4F |
Mean |
24 |
25 |
20** |
23** |
25* |
25 |
|
|
|
SD |
2.1 |
2.1 |
1.8 |
2.0 |
2.1 |
2.4 |
|
|
|
N |
20 |
20 |
20 |
20 |
20 |
20 |
|
Table 7.8.2/5: Organ weights - group mean unadjusted and adjusted values (g)
Group/Sex |
|
Terminal Body Weight |
Liver weight |
|
Unadjusted Means Statistical test: |
|
Wi |
|
|
1F |
Mean |
420 |
18.17 |
|
|
SD |
20 |
1.47 |
|
|
N |
20 |
20 |
|
2F |
Mean |
425 |
18.48 |
|
|
SD |
18 |
1.45 |
|
|
N |
20 |
20 |
|
3F |
Mean |
420 |
18.37 |
|
|
SD |
23 |
1.44 |
|
|
N |
19 |
19 |
|
4F |
Mean |
404* |
19.14 |
|
|
SD |
18 |
1.56 |
|
|
N |
20 |
20 |
|
Adjusted Means Statistical test: |
|
|
Wi |
|
1F |
Mean |
|
18.02 |
|
2F |
Mean |
|
18.06 |
|
3F |
Mean |
|
18.22 |
|
4F |
Mean |
|
19.84** |
|
Table 7.8.2/6: Gravid uterine weight, adjusted body weight and adjusted body weight change - group mean values (g)
|
|||||||||
Group/Sex |
|
Body weight on Day 6 |
Terminal Body weight on Day 20 |
Body weight Change Days 6-20 |
Gravid Uterine Weight |
Adjusted Body weight Day 20 |
Adjusted Body weight Change Days 6-20 |
||
Statistical test |
|
Av |
Wi |
Wi |
Wi |
Wi |
Wi |
||
1F |
Mean |
292 |
420 |
128 |
95 |
325 |
33 |
||
|
SD |
11.1 |
20.4 |
13.6 |
10.4 |
16.9 |
8.8 |
||
|
N |
20 |
20 |
20 |
20 |
20 |
20 |
||
2F |
Mean |
294 |
425 |
131 |
95 |
330 |
37 |
|
|
|
SD |
10.1 |
18.1 |
13.2 |
11.6 |
12.8 |
8.3 |
|
|
|
N |
20 |
20 |
20 |
20 |
20 |
20 |
|
|
3F |
Mean |
291 |
420 |
129 |
94 |
326 |
35 |
|
|
|
SD |
12.9 |
11.9 |
14.5 |
14.6 |
19.4 |
10.3 |
|
|
|
N |
19 |
19 |
19 |
19 |
19 |
19 |
|
|
4F |
Mean |
286 |
404* |
118* |
89 |
315 |
28 |
|
|
|
SD |
11.7 |
18.1 |
11.6 |
11.9 |
14.6 |
8.6 |
|
|
|
N |
20 |
20 |
20 |
20 |
20 |
20 |
|
Applicant's summary and conclusion
- Conclusions:
- The No Observed Adverse Effect Level (NOAEL) of Terpineol multiconstituent was considered to be 600 mg/kg bw/day for maternal toxicity and 600 mg/kg bw/day for developmental toxicity in Sprague-Dawley rats.
- Executive summary:
In a GLP-compliant prenatal developmental toxicity study performed according to OECD guideline 414, Terpineol multiconstituent diluted in corn oil was administered by gavage to groups of mated female Sprague-Dawley rats (20 mated females/dose) at the dose levels of 0, 60, 200, 600 mg /kg bw/ day from Days 6 to 19 after mating. Animals were inspected visually at least twice daily for evidence of ill-health or reaction to treatment. Detailed observations were recorded daily at the following times in relation to dose administration. A detailed physical examination was performed on each animal on Days 0, 5, 12, 18 and 20 after mating to monitor general health. The weight of each adult was recorded on Days 0, 3 and and then daily from Days 6 to 20 after mating. The weight of food supplied to each adult, that remaining and an estimate of any spilled was recorded for the periods Days 0-2, 3-5, 6-9, 10-13, 14-17 and 18-19 inclusive after mating.
On Day 20 post-coitum, the dams were sacrificed and subjected to macroscopic examination. The gravid uterine weight, number of implantations, live and dead fetuses, early and late resorptions and corpora lutea were recorded. Gross evaluation of the placenta was also performed.
Fetuses were sexed, weighed and examined for external, soft tissue and skeletal malformations.
With the exception of one female in the 200 mg/kg bw/day group (No. 52) which had a total litter resorption, all females were found to be pregnant with live young at scheduled termination on Day 20 of gestation. No mortality was observed.
At scheduled termination on Day 20 of gestation, the adjusted mean liver weight of females receiving 600 mg/kg bw/day was significantly higher than Control (1.10X Control). There were no treatment-related macroscopic abnormalities detected. No relevant clinical signs or signs of reaction to treatment were noted in treated females. Females receiving 60 or 200 mg/kg bw/day showed no treatment-related changes in clinical condition, body weight performance, food intake, liver weight or macropathology.
There was no effect of maternal treatment with Terpineol multiconstituent at any dose level investigated on litter data. Sex ratio, as assessed by the percentage of males per litter, was generally comparable in all groups and in line with expectations. Embryo-fetal growth was slightly reduced by maternal treatment at 600 mg/kg bw/day.
It was considered that there was no adverse effect of maternal treatment on embryo-fetal development; the incidence of major and minor abnormalities and skeletal variants showed no relationship to maternal treatment with Terpineol multiconstituent.
In the 600 mg/kg bw/day group there was a slightly higher incidence of incompletely ossified or unossified 5th and/or 6th sternebrae compared to concurrent control and the Historical Control Data range.
It was considered that this minor finding did not constitute an adverse effect on development.
On the basis of the results obtained in this study, the dosage of 600 mg/kg bw/day was considered to be the NOAEL (No Observed Adverse Effect Level) for maternal toxicity. The NOAEL for developmental toxicity was considered to be 600 mg/kg bw/day.
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