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EC number: 216-133-4 | CAS number: 1506-02-1
- 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
Developmental toxicity / teratogenicity
Administrative data
- Endpoint:
- developmental toxicity
- Type of information:
- experimental study
- Adequacy of study:
- weight of evidence
- Study period:
- 04 Sep 2018 to 13 Dec 2018
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- guideline study
Data source
Reference
- Reference Type:
- study report
- Title:
- Unnamed
- Year:
- 2 018
- Report date:
- 2018
Materials and methods
Test guideline
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 414 (Prenatal Developmental Toxicity Study)
- Version / remarks:
- adopted on 25 June 2018
- Deviations:
- no
- GLP compliance:
- yes (incl. QA statement)
- Limit test:
- no
Test material
- Reference substance name:
- 1-(5,6,7,8-tetrahydro-3,5,5,6,8,8-hexamethyl-2-naphthyl)ethan-1-one
- EC Number:
- 216-133-4
- EC Name:
- 1-(5,6,7,8-tetrahydro-3,5,5,6,8,8-hexamethyl-2-naphthyl)ethan-1-one
- Cas Number:
- 1506-02-1
- Molecular formula:
- C18H26O
- IUPAC Name:
- 1-(5,6,7,8-tetrahydro-3,5,5,6,8,8-hexamethyl-2-naphthyl)ethan-1-one
- Test material form:
- solid
- Details on test material:
- Purity: 98%
Constituent 1
- Specific details on test material used for the study:
- SOURCE OF TEST MATERIAL
- Lot/batch No.of test material: 0000145096
- Expiration date of the lot/batch: 03-01-2020
- Purity test date: 98%
STABILITY AND STORAGE CONDITIONS OF TEST MATERIAL
- Storage condition of test material: Ambient (+15 to +25ºC)
- Solubility and stability of the test substance in the solvent/vehicle: Based on results of validation study, the test material formulations prepared at 1.0 and 250 mg/mL in the vehicle (Corn oil) are stable and resuspendable in the vehicle for 3 days when stored at room temperature at both the concentrations.
Test animals
- Species:
- rabbit
- Strain:
- New Zealand White
- Details on test animals or test system and environmental conditions:
- TEST ANIMALS
- Source: Geniron Biolabs Pvt. Ltd., No.93, Solur, Thally Road, Anekal, Bengaluru-562106, India
- Age at study initiation: 7 months young adult, nulliparous and non-pregnant females at the initiation of the study and adult males (for mating purpose only).
- Weight at study initiation: G1: 2.975 ± 0.20, G2: 2.938 ± 0.21, G3: 2.984 ± 0.20, G4: 2.995 ± 0.20
- Housing: The rabbits were housed individually, except during cohabitation, when the females rabbits were cohabited with the males in 1:1 ratio in rabbit cages (approximate size: Length 65 cm x BWidth 65 cm x Height 45 cm) with shallow cage body and facilities for providing pelleted food (Stainless steel feed hopper) and drinking water in bottle fitted with sipper tube. The waste collection tray was changed daily (except on Sundays and public holidays). - Diet: Rabbit feed manufactured by Special Diets Services, Essex, England (Batch No.3439) was provided ad libitum in stainless steel feed hoppers to rabbits.
- Water: Deep bore-well water passed through activated charcoal filter and exposed to UV rays in Aquaguard water filter-cum-purifier was provided ad libitum in polycarbonate bottles with stainless steel sipper tubes to rabbits.
- Acclimation period: After clinical examination for good health and suitability for the study, the rabbits were acclimatized for five days before initiation of mating. During the acclimatization period, all rabbits were observed at least once daily.
ENVIRONMENTAL CONDITIONS
- Temperature (°C): 20 - 21
- Humidity (%): 64-65, The relative humidity in the experimental rooms was calculated daily from dry and wet bulb temperature recordings.
- Air changes (per hr): 12-15
- Photoperiod (hrs dark / hrs light): 12/12
Administration / exposure
- Route of administration:
- oral: gavage
- Vehicle:
- corn oil
- Details on exposure:
- PREPARATION OF DOSING SOLUTIONS:
The test material dose formulations were prepared prior to treatment and used within the stability period. Required quantities of the test item were weighed separately for each dose group and transferred into separate mortars. The test item was triturated gently using a pestle to obtain a fine powder. A small portion of the vehicle (Corn oil) was added and the contents was triturated well to obtain a suspension. This suspension was transferred into a pre-marked beaker (Previously calibrated to the desired volume). The mortar and pestle was rinsed with the vehicle and the contents were transferred to the same pre-marked beaker. The suspension was made up to the intended volume with the vehicle. The homogeneity of the the test material dosing suspension during oral gavage was maintained by constant stirring using a magnetic stirrer.
VEHICLE
- Justification for use and choice of vehicle: Corn oil was selected as vehicle for preparing the test material formulations in this study, as the same vehicle was used in pilot rabbit study without any effects.
- Concentration in vehicle: 0 mg/mL, 2.5 mg/mL, 7.5 mg/mL, 25 mg/mL
- Amount of vehicle: 2 mL/kg bw
-The dosing was performed using a suction catheter attached to a plastic disposable syringe from GD 6 to GD 28 of presumed gestation. The actual volume administered was calculated based on the most recent body weight on first day of treatment (Gestation Day 6) and was adjusted according to the most recent body weights recorded till Gestation Day 28. Dose formulations were continuously stirred during dose administrations. The animals in the vehicle control group were handled and administered vehicle in an identical manner to the treatment groups. - Analytical verification of doses or concentrations:
- yes
- Details on analytical verification of doses or concentrations:
- For homogeneity and concentration analysis of test material, the prepared formulations were sampled at the initiation of treatment (GD 6) and at termination of treatment period (GD 28). Samples were drawn at each dose level (two samples from the top, middle and bottom layers) in duplicate sets. Similarly, samples only from middle layer was collected from vehicle control. The analyses was done using a validated analytical method. One set of samples was analyzed for concentration and other set of samples was kept as a backup at room temperature for reanalysis. These samples were discarded as the results of first set of samples were within the acceptable limits. Formulations were considered acceptable as the mean result for all layers was within ± 15% of the nominal concentration.
- Details on mating procedure:
- - Impregnation procedure: cohoused
- M/F ratio per cage: During the mating period, females were cohabited randomly with males in a 1:1 ratio
- Proof of pregnancy: After confirmation of mating by visual examination, the day was referred to as day 0 of pregnancy - Duration of treatment / exposure:
- The dosing was performed using a suction catheter attached to a plastic disposable syringe from GD 6 to GD 28 of presumed gestation.
- Frequency of treatment:
- Once per day
- Duration of test:
- All animals surviving until scheduled euthanasia were euthanised on day 29 post-coitum.
Doses / concentrationsopen allclose all
- Dose / conc.:
- 5 mg/kg bw/day (actual dose received)
- Remarks:
- Low dose
- Dose / conc.:
- 15 mg/kg bw/day (actual dose received)
- Remarks:
- Mid dose
- Dose / conc.:
- 50 mg/kg bw/day (actual dose received)
- Remarks:
- High dose
- No. of animals per sex per dose:
- Total of 92 female rabbits were mated and allocated to a control group and 3 treatment groups (23 female rabbits/ group). Male rabbits were used only for mating.
- Control animals:
- yes, concurrent vehicle
- Details on study design:
- Selection of Dose Levels and Dose Justification: A preliminary dose range finding study (DRF) in pregnant female New Zealand White rabbits was carried out using 6 rabbits per group with test material dosed at 5, 15 and 50 mg/kg bw/day along with the concurrent vehicle control group. The rabbits were treated once daily with test item formulations by oral gavage at a dose volume of 2 mL/kg body weight from GD 6 to 28 and observed for clinical signs and mortality. The test material at 5 mg/kg bw/day did not affect body weight, food consumption, and maternal and litter data parameters. At 15 mg/kg bw/day, body weight and food consumption were not affected, but there was reduction in mean fetal weights observed. Treatment at 50 mg/kg bw/day resulted in reduction in food consumption and there was reduction in uterine weight observed further causing reduction in the mean litter weights. These findings were considered test material treatment related. Gross evaluation of the placenta revealed no findings. No abnormality was noticed on external observations of fetuses at any of the doses tested. Based on the results of the dose range finding study and in consultation 0, 5, 15 and 50 mg/kg/day dose levels were selected for the definitive study.
Examinations
- Maternal examinations:
- CLINICAL SIGNS AND MORTALITY:
- Clinical Signs and Mortality: All rabbits were observed for morbidity and mortality twice daily, i.e. once in the morning and once in the afternoon. Rabbits were observed for clinical signs during the treatment period of the study: pre dose and post dose (within 1- 2 hours of administration). On 20 September 2018, post dose observation was delayed by approximately 4.00 hrs. Aborted rabbits were necropsied, and gross observations observed were recorded.
BODY WEIGHT:
- All the females included in the study (G1 to G4) were weighed on GD 0, 3, 6, 9, 12, 15, 18, 21, 24, 27 and 29. The intermittent body weight gain was calculated for GD 0 - 3, 3 - 6, 6 - 9, 9 - 12, 12 - 15, 15 - 18, 18 - 21, 21 - 24, 24 - 27 and 27 - 29. Further the body weight gain for pre-treatment period (GD 0 to 6), treatment period (GD 6 to 28), and for entire gestation period (GD 0 to 29) was derived and statistically analyzed only for rabbits pregnant at caesarean section. The corrected body weight (carcass weight) was obtained by subtracting the unopened uterine weight from terminal body weight (body weight on GD 29). The corrected body weight gain was calculated by subtracting the body weight on GD 6 from corrected body weight.
FOOD CONSUMPTION:
- About 600 g of food (food input) was provided on GD 0. The left over food was recorded and replenished to about 600 g on GD 3, 6, 9, 12, 15, 18, 21, 24 and 27. Prior to terminal sacrifice, left over food was recorded on GD 29 of presumed gestation. There was no spillage of food noticed during the entire study period. Intermittent food consumption i.e GD 0 - 3, 3 - 6, 6 - 9, 9 - 12, 12 - 15, 15 - 18, 18 - 21, 21 -24, 24 - 27 and 27 - 29 was calculated. Further, food intake for pre-treatment (GD 0 to 6), treatment (GD 6 to 29), and for entire gestation period (GD 0 to 29) was derived and statistically analyzed only for rabbits pregnant at caesarean section.
NECROPSY:
- Prior to caesarean section, random numbers were generated for coding to avoid bias during caesarean section and subsequent fetal evaluations. The animal code was written on the ear and the permanent accession number was striked out. On GD 29, all the rabbits were sacrificed by intravenous injection of sodium thiopentone. Gross pathological changes of all external and visceral organs of dams, including uterine contents were recorded. - Ovaries and uterine content:
- The ovaries and uterine content was examined after termination: Yes
Examinations included:
- Gravid uterus weight: Yes
- Number of corpora lutea: Yes
- Number of implantations: Yes
- Number of early resorptions: Yes
- Number of late resorptions: Yes
- Other: gross evaluation of placenta - Fetal examinations:
- - External examinations: Yes: all per litter
- Soft tissue examinations: Yes: all per litter
- Skeletal examinations: Yes: all per litter
- Head examinations: Yes: half per litter - Statistics:
- The data on maternal body weight and food consumption, interval body weight changes, gravid uterine weight, body weight change corrected to gravid uterine weight were analyzed using Analysis of Variance (ANOVA) after testing for homogeneity for intra group variance using Levene’s test. Where intra group variances were heterogeneous, ANOVA was performed after suitable transformation of data. Dunnett’s pairwise comparison of the treated group means with the control group mean was performed, when the group differences were found significant. Fetal weight for male and female was analyzed using Analysis of Covariance (ANCOVA) taking litter size as covariate for group. Number of corpora lutea, number of implantations, early and late resorptions, pre-implantation and post-implantation loss, external, visceral and skeletal observations for variations were analyzed using Kruskal Wallis test for group comparison. Mann-Whitney/Wilcoxon test pair wise comparisons of the treated groups with the control group was performed, when the group differences were significant. The incidence of dams with and without resorptions was tested using Cochran Armitage trend test followed by Fisher’s exact test for group association.
- Indices:
- All the indices can be found in the field 'Any other information on materials and methods, incl. tables'.
Results and discussion
Results: maternal animals
General toxicity (maternal animals)
- Clinical signs:
- no effects observed
- Description (incidence and severity):
- There were no clinical signs observed at any of the doses tested during the study period.
- Dermal irritation (if dermal study):
- not examined
- Mortality:
- no mortality observed
- Body weight and weight changes:
- effects observed, treatment-related
- Description (incidence and severity):
- There was no change in mean maternal (corrected) body weights and (corrected) body weight gains during the different periods of gestation (GD 0-6; GD 6-29; GD 0-29) of the rabbits treated at 5 and 15 mg/kg/day compared to the vehicle control group. At 50 mg/kg/day there was statistically significant decrease in body weight gain during GD 6-29 (116%) and GD 0 – 29 (79%). In addition, there was a trend towards a decrease in mean maternal (corrected) body weight and corrected body weight gain, which was not statistically significant.
- Food consumption and compound intake (if feeding study):
- effects observed, treatment-related
- Description (incidence and severity):
- Compared to the vehicle control group, there was no change in food consumption of rabbits dosed at 5 and 15 mg/kg/day. Though not significant, there was a trend for a decrease in food consumption during different periods of gestation with stastistical significance during GD 21-24 at 50 mg/kg/day. The reduction in body weight and food consumption at 50 mg/kg/day is considered a treatment-related effect.
- Food efficiency:
- not examined
- Water consumption and compound intake (if drinking water study):
- 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 50 mg/kg/day compared with the vehicle control, there was a decrease in uterine weight (25%).
- Gross pathological findings:
- effects observed, non-treatment-related
- Description (incidence and severity):
- There were no gross pathological findings in any of the treated groups except for a single occurrence of pale liver at 15 and 50 mg/kg/day.
- 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:
- effects observed, non-treatment-related
- Description (incidence and severity):
- There were incidental occurrences of abortion in each of the low mid and high dose groups. One animal per group.
- Pre- and post-implantation loss:
- effects observed, treatment-related
- Description (incidence and severity):
- At 50 mg/kg/day compared with the vehicle control, there was an increase in post implantation loss.
- Total litter losses by resorption:
- effects observed, treatment-related
- Description (incidence and severity):
- Two pregnant dams at the high dose of 50 mg/kg/day had complete resorptions.
- Early or late resorptions:
- effects observed, treatment-related
- Description (incidence and severity):
- At 50 mg/kg/day compared with the vehicle control, there was an increase in dams with resorptions.
- Dead fetuses:
- no effects observed
- Description (incidence and severity):
- No dead fetuses were found in any of the dose groups
- Changes in pregnancy duration:
- no effects observed
- Changes in number of pregnant:
- effects observed, non-treatment-related
- Description (incidence and severity):
- The number of rabbits sacrificed at term were 23, 22, 22 and 22, respectively, of which 2, 2, 2 and 3 rabbits were non pregnant. The number of pregnant rabbits in the vehicle control, low, mid and high dose groups were 21, 20, 20 and 19, respectively.
- Other effects:
- not examined
Effect levels (maternal animals)
open allclose all
- Key result
- Dose descriptor:
- NOAEL
- Remarks:
- maternal general toxicity
- Effect level:
- 15 mg/kg bw/day (actual dose received)
- Based on:
- test mat.
- Basis for effect level:
- body weight and weight gain
- food consumption and compound intake
- Key result
- Dose descriptor:
- NOAEL
- Remarks:
- maternal developmental toxicity
- Effect level:
- 15 mg/kg bw/day (actual dose received)
- Based on:
- test mat.
- Basis for effect level:
- necropsy findings
- pre and post implantation loss
- total litter losses by resorption
Maternal abnormalities
- Key result
- Abnormalities:
- no effects observed
Results (fetuses)
- Fetal body weight changes:
- effects observed, treatment-related
- Description (incidence and severity):
- At 50 mg/kg/day, there was a significant reduction in mean fetal weights (-8.3%) at both the sexes (males and females) as compared to the vehicle control group.
- Reduction in number of live offspring:
- no effects observed
- Description (incidence and severity):
- The total number of fetuses were 135, 122, 118 and 94 at 0, 5, 15 and 50 mg/kg/day, respectively.
- Changes in sex ratio:
- no effects observed
- Description (incidence and severity):
- Information can be found in Table 1 in the field 'Any other information on results, incl. tables'.
- Changes in litter size and weights:
- no effects observed
- Changes in postnatal survival:
- not examined
- External malformations:
- effects observed, non-treatment-related
- Description (incidence and severity):
- No test item related major abnormality was observed during external observations of the fetuses at any of the doses. Anomaly of fore limb flexed at wrist (moderate) was observed in one fetus of a litter with 5 fetuses at 50 mg/kg bw/day and in one fetus of a litter with 8 fetuses in the vehicle control group. These minor changes were considered incidental and not adverse as these observations commonly occur in animals of this test model. The incidence is attributed to random occurrence and not treatment related.
- Skeletal malformations:
- effects observed, non-treatment-related
- Description (incidence and severity):
- There were no test item related skeletal malformations observed in fetuses of dams treated up to 50 mg/kg/day. Variants and anomalies observed across vehicle and treated groups were comparable and are consistent with concurrent and historical data. The variants and anomalies were consistent with concurrent and historical data.
- Visceral malformations:
- effects observed, treatment-related
- Description (incidence and severity):
- There were no test item related major visceral malformations observed in fetuses of dams treated up to 50 mg/kg/day. Anomalies such as gall bladder hypoplastic in vehicle and test material treated groups, and bilobed gall bladder in the vehicle control group were observed. These findings were not considered adverse as these observations commonly occur in animals of this test model and the incidence of occurrence were consistent with concurrent or historical controls. At 50 mg/kg bw/day, visceral evaluation showed incidences of unilateral absence of kidney and ureter in one dam and unilateral dilated ureter with hydroneprosis in another dam. These findings (2/94 fetuses and 2/17 litters) were considered developmental anomalies.
- Other effects:
- no effects observed
- Description (incidence and severity):
- Gross evaluation of the placenta revealed no findings. External and visceral and skeletal examination of fetuses revealed no signs of teratogenicity.
Effect levels (fetuses)
- Key result
- Dose descriptor:
- NOAEL
- Remarks:
- Developmental Toxicity
- Effect level:
- 15 mg/kg bw/day
- Based on:
- test mat.
- Sex:
- male/female
- Basis for effect level:
- fetal/pup body weight changes
- visceral malformations
Fetal abnormalities
- Key result
- Abnormalities:
- no effects observed
Overall developmental toxicity
- Key result
- Developmental effects observed:
- yes
- Lowest effective dose / conc.:
- 15 mg/kg bw/day
- Treatment related:
- yes
- Relation to maternal toxicity:
- developmental effects as a secondary non-specific consequence of maternal toxicity effects
- Dose response relationship:
- yes
Any other information on results incl. tables
For homogeneity and concentration analysis of test material it was found that the relative standard deviation of assay of top, middle and bottom layer (total 6 samples) was less than or equal to 10%.
Table 1. Summary of Litter data
Sex: female |
G1 0 mg/kg/day |
G2 5 mg/kg/day |
G3 15 mg/kg/day |
G4 50 mg/kg/day |
|
Pregnant |
N |
21 |
20 |
21 |
19 |
Total number of fetuses |
Mean N Sum |
6.4 21 135.0 |
6.0 20 119.0 |
5.9 20 118.0 |
5.5 17 94.0 |
% Male Fetuses |
|
60.0 |
45.4 |
48.3 |
43.6 |
Dead |
Sum |
0 |
0 |
0 |
0 |
Live Male |
Sum |
81 |
55 |
57 |
41 |
Mean fetal [c] weight (M) (g) |
Mean SD N |
39.61 5.20 21 |
39.82 4.77 20 |
38.02 5.59 20 |
35.94 7.38 16 |
Live Female |
Sum |
54 |
67 |
61 |
53 |
Mean fetal [c1] weight (F) (g) |
Mean SD N |
40.22 6.24 21 |
39.83 4.78 20 |
37.13 4.22 20 |
36.03 7.26 17 |
Live fetuses |
Sum |
135 |
122 |
118 |
94 |
Mean fetal [c2] weight (both) (g) |
Mean SD N |
39.81 5.32 21 |
39.79 4.47 20 |
37.50 4.38 20 |
36.51* 7.21 17 |
[c] – Anova/Anova&Dunnett
{Covariate(s): Number of Live Male Fetuses}
[c1] - Anova/Anova&Dunnett
{Covariate(s): Number of Live Female Fetuses}
[c2] - Anova/Anova&Dunnett
{Covariate(s): Number of both Fetuses}; *=p<0.05
Table 2. Summarized Details of Necropsy
Parameters |
Group No. & |
G1 |
G2 |
G3 |
G4 |
Dose (mg/kg/day) |
0 |
5 |
15 |
50 |
|
Total No. of rabbits / group |
23 |
23 |
23 |
23 |
|
Duration of treatment |
GD 6 to 28 (total 23 days) |
||||
Caesarean section (day of presumed gestation) |
29 |
||||
Number of rabbits sacrificed at caesarean section |
23 |
22 |
22 |
22 |
|
Number of rabbits aborted |
0 |
1 |
1 |
1 |
|
Number of rabbits non-pregnant at caesarean section |
2 |
2 |
2 |
3 |
|
Number of rabbits pregnant at caesarean section Number of rabbits with complete resorption |
21 0 |
20 0 |
20 0 |
19 2 |
|
Number of litters examined |
21 |
20 |
20 |
17 |
|
Total number of fetuses |
135 |
122 |
118 |
94 |
|
|
|
|
|
|
|
Number of fetuses evaluated |
|
|
|
|
|
External, visceral and skeletal |
135 |
122 |
118 |
94 |
|
Number of fetus for decapitation |
61 |
54 |
55 |
44 |
|
Number of intact fetuses |
74 |
68 |
63 |
50 |
Table 3. Summary of Maternal Body Weight of Pregnant Rabbits
Sex: Female
Day(s) |
G1 0 mg/kg/day |
G1 5 mg/kg/day |
G1 15 mg/kg/day |
G1 50 mg/kg/day |
||
Body Weight (kg) |
0 [a] |
Mean SD N |
2.9731 0.2061 21 |
3.0035 0.2150 20 |
2.9701 0.2116 20 |
2.9880 0.1671 19 |
3 [a] |
Mean SD N |
3.0049 0.2171 21 |
3.0608 0.2312 20 |
2.9842 0.2261 20 |
3.0354 0.2011 19 |
|
6 [a] |
Mean SD N |
3.0279 0.2159 21 |
3.0947 0.2496 20 |
3.0148 0.2489 20 |
3.0541 0.1908 19 |
|
9[a] |
Mean SD N |
2.9963 0.2104 21 |
3.0166 0.2102 20 |
2.9551 0.2423 20 |
2.9587 0.1932 19 |
|
12 [a] |
Mean SD N |
3.0370 0.2183 21 |
3.0246 0.2512 20 |
2.9803 0.2381 20 |
2.9600 0.2331 19 |
|
15 [a] |
Mean SD N |
3.0925 0.2588 21 |
3.0756 0.2707 20 |
2.9968 0.2844 20 |
2.9672 0.1995 19 |
|
18 [a] |
Mean SD N |
3.1110 0.2546 21 |
3.1034 0.2673 20 |
2.9996 0.2799 20 |
2.9928 0.2294 19 |
|
21 [a] |
Mean SD N |
3.1415 0.2842 21 |
3.1024 0.2706 20 |
3.0086 0.2724 20 |
2.9965 0.2373 19 |
|
24 [a] |
Mean SD N |
3.1610 0.2899 21 |
3.1264 0.2659 20 |
3.0384 0.2709 20 |
3.0274 0.2524 19 |
|
27 [a] |
Mean SD N |
3.1636 0.3142 21 |
3.1256 0.2557 20 |
3.0443 0.2493 20 |
3.0205 0.2254 19 |
|
29 [a] |
Mean SD N |
3.1781 0.3041 21 |
3.1374 0.2504 20 |
3.0505 0.2179 20 |
3.0307 0.2454 19 |
[a] – Anova & Dunnett(Log)
Table 4. Summary of Maternal Body Weight Gain of Pregnant Rabbits
Sex: Female
Day(s) |
G1 0 mg/kg/day |
G1 5 mg/kg/day |
G1 15 mg/kg/day |
G1 50 mg/kg/day |
|||
Absolute Weight Gain (kg) |
0 -> 3 [a] |
Mean SD N |
0.0318 0.0641 21 |
0.0573 0.0374 20 |
0.0140 0.0830 20 |
0.0475 0.0734 19 |
|
3 -> 6 [a1] |
Mean SD N |
0.0230 0.0527 21 |
0.0340 0.0395 20 |
0.0307 0.0494 20 |
0.0186 0.0431 19 |
|
|
6 -> 9 [a1] |
Mean SD N |
-0.0316 0.0778 21 |
-0.0781 0.0876 20 |
-0.0598 0.0743 20 |
-0.0953 0.0759 19 |
|
|
9 -> 12 [a1] |
Mean SD N |
0.0407 0.0855 21 |
0.0080 0.0967 20 |
0.0252 0.0856 20 |
0.0012 0.0840 19 |
|
|
12 -> 15 [a] |
Mean SD N |
0.0554 0.0740 21 |
0.0510 0.0720 20 |
0.0165 0.0925 20 |
0.0072 0.1001 19 |
|
|
15 -> 18 [a1] |
Mean SD N |
0.0185 0.0664 21 |
0.0279 0.0513 20 |
0.0028 0.0775 20 |
0.0256 0.0610 19 |
|
|
18 -> 21 [a] |
Mean SD N |
0.0306 0.0493 21 |
-0.0010 0.0447 20 |
0.0090 0.0757 20 |
0.0036 0.0461 19 |
|
|
21 -> 24 [a1] |
Mean SD N |
0.0194 0.0457 21 |
0.0240 0.0361 20 |
0.0298 0.0584 20 |
0.0309 0.0598 19 |
|
|
24 -> 27 [a1] |
Mean SD N |
0.0026 0.0701 21 |
-0.0007 0.0483 20 |
0.0059 0.0570 20 |
-0.0069 0.0486 19 |
|
|
27 -> 29 [a1] |
Mean SD N |
0.0145 0.0401 21 |
0.0118 0.0612 20 |
0.0062 0.0560 20 |
0.0102 0.0465 19 |
|
|
0 -> 6 [a] |
Mean SD N |
0.0548 0.0832 21 |
0.0912 0.0583 20 |
0.0447 0.0950 20 |
0.0661 0.0705 19 |
|
|
6 -> 29 [a1] |
Mean SD N |
0.1502 0.2006 21 |
0.0427 0.1361 20 |
0.0357 0.1844 20 |
-0.0234* 0.1614 19 |
|
|
0 -> 29 [a] |
Mean SD N |
0.2050 0.2326 21 |
0.1339 0.1331 20 |
0.0804 0.1645 20 |
0.0427* 0.1894 19 |
|
|
Corrected/adjusted Body weight (kg) |
GD29 - gravid uterine. Wt [a2] |
Mean SD N |
2.8132 0.2704 21 |
2.7880 0.2443 20 |
2.7093 0.1993 20 |
2.7586 0.2638 19 |
|
Corrected/adjusted Body weight Gain |
Corrected Bwt-GD6 [a1] |
Mean SD N |
-0.2147 0.1931 21 |
-0.3067 0.1271 20 |
-0.3055 0.1611 20 |
-0.2954 0.1820 19 |
|
[a] – Anova & Dunnett: *= p<0.05
[a1] – Anova & Dunnett(Rank): *= p<0.05
[a2] – Anova & Dunnett(Log)
Table 5. Summary of Maternal Data
Sex: Female
Day(s) Relative to mating |
G1 0 mg/kg/day |
G1 5 mg/kg/day |
G1 15 mg/kg/day |
G1 50 mg/kg/day |
||
Group size |
GD 29 |
N |
23 |
23 |
23 |
23 |
Pregnant |
GD 29 |
N |
21 |
20 |
20 |
19 |
Gravid Uterus (g) |
GD 29 [a] |
Mean SD N |
364.9 79.9 21 |
349.4 62.5 20 |
341.3 64.4 20 |
286.1** 88.2 17 |
Number of CorporaLutea |
GD 29 [k] |
Mean SD N |
8.2 1.4 21 |
8.1 1.4 20 |
8.4 2.0 20 |
8.2 1.9 17 |
Number of Implantation |
GD 29 [k] |
Mean SD N |
7.0 1.7 21 |
6.6 1.2 20 |
6.6 1.8 20 |
6.4 2.0 17 |
With Early resorption |
GD 29 |
Total N |
21 4 |
20 5 |
20 6 |
17 6 |
Number of Early Deaths |
GD 29 [k] |
Mean SD N Sum |
0.2 0.5 21 5.0 |
0.3 0.6 20 6.0 |
0.4 0.6 20 7.0 |
0.4 0.5 17 6.0 |
With Late Resorptions |
GD 29 |
Total N |
21 4 |
20 4 |
20 6 |
17 7 |
Number of Late deaths |
GD 29 [k] |
Mean SD N Sum |
0.3 0.7 21 6.0 |
0.2 0.4 20 4.0 |
0.3 0.5 20 6.0 |
0.5 0.6 17 8.0 |
With Resorptions |
GD 29 |
N N-ve N+ve |
21 13 8 |
20 11 9 |
20 9 11 |
17 5 12 |
Total number of resorptions |
GD 29 [f] |
Mean SD N Sum Trend |
0.5 0.8 21 11.0 . |
0.4 0.6 20 10.0 . |
0.7 0.7 20 13.0 0.1969. |
0.8 0.6 17 14.0 0.0454* |
Pre-imp Loss / Animal |
GD 29 [k] |
Mean SD N |
1.24 0.94 21 |
1.50 1.05 20 |
1.85 1.25 20 |
1.82 1.63 17 |
[a] – Anova & Dunnett(Log)
[k] – Kruskal-Wallis & Wilcoxon
[f] – Cochran Armitage, Chi-Squared & Chi squared - Pearson
Applicant's summary and conclusion
- Conclusions:
- In this study, which conducted based on OECD TG 414 and under GLP conditions, prenatal developmental toxicity of the test material was evaluated in New Zealand White rabbits following daily administration by oral gavage at 0, 5, 15 and 50 mg/kg/day during gestation days 6 to 28. External and visceral and skeletal examination of fetuses revealed no signs of teratogenicity. Based on the above findings, the No- Observed- Adverse- Effect Level (NOAEL) are as follows:
- NOAEL maternal general toxicity is 15 mg/kg/day
- NOAEL maternal developmental toxicity is 15 mg/kg/day
- NOAEL developmental toxicity is 15 mg/kg/day - Executive summary:
The objective of this study was to evaluate the prenatal developmental toxicity of the test material when administered daily by oral gavage during gestation days (GD) 6 to 28 to presumed pregnant New Zealand White rabbits.This study evaluated the maternal toxicity and adverse effects on development of the embryo and fetus in pregnant female rabbits. Mated female rabbits were assigned to four groups with 23 animals in each group. The day on which mating had occurred was considered as gestation Day 0 (GD 0) for each individual female rabbit. Test material in vehicle (Corn oil) was administered at 0, 5, 15 and 50 mg/kg/day. The control group received the vehicle only. Dose formulation analysison initiation and termination of treatment periodindicated all samples were within 15% of the nominal concentrations. All rabbits were observed for clinical signs, morbidity and mortality, body weight changes and food consumption.Caesarean section was performed for all the surviving rabbits on GD 29 and dams were examined for gross pathological changes. The uterus was removed by laparotomy, weighed and the contents were examined for number of implantation sites, early and late resorptions and number of fetuses.The number of corpora lutea in ovaries was counted. All the fetuses were sexed, weighed and examined for external malformations. All the live fetuses were examined forvisceral and skeletal variations and malformations. The main findings of the study are presented below:
There were no mortalities, clinical signs or gross necropsy findings at any of the doses tested except for incidental abortions in each of the, low, mid and high dose groups. Mean body weight gain at 50 mg/kg/day was lower compared to the vehicle control animals. Food consumption at 50 mg/kg/day was reduced during treatment period (GD 6 to 28). At 50 mg/kg/day there was a reduction in uterine weight, increase in post implantation loss and two dams with complete resorptions. At 50 mg/kg/day a significant reduction in litter weight was observed. Visceral evaluation at 50 mg/kg/day showed incidences (2/94 fetus) of unilateral absence of kidney and ureter and ureter dilated with hydronephrosis.
In conclusion, based on the above findings, the No- Observed- Adverse- Effect Level (NOAEL) for maternal and fetal developmental toxicity is 15 mg/kg/day.
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