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EC number: 800-696-3 | CAS number: 78605-96-6
- 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:
- 29 December 2018 - April 2019
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- guideline study
- Remarks:
- The study was conducted to according to GLP and followed international guideline
Data source
Reference
- Reference Type:
- study report
- Title:
- Unnamed
- Year:
- 2 019
Materials and methods
Test guideline
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 414 (Prenatal Developmental Toxicity Study)
- Version / remarks:
- 2018
- Deviations:
- yes
- Remarks:
- The observation for clinical signs was delayed by approximately 40 minutes.
- GLP compliance:
- yes (incl. QA statement)
- Limit test:
- no
Test material
- Reference substance name:
- Heptanal, 2-(phenylmethylene)-, (2E)-
- EC Number:
- 800-696-3
- Cas Number:
- 78605-96-6
- Molecular formula:
- C14 H18 O
- IUPAC Name:
- Heptanal, 2-(phenylmethylene)-, (2E)-
- Test material form:
- liquid
Constituent 1
- Specific details on test material used for the study:
- SOURCE OF TEST MATERIAL
- Source and lot/batch No.of test material: Tennants Fine Chemicals Ltd, Batch no;51757 / 45562
- Expiration date of the lot/batch:15th October 2020
- Purity test date: 98.43%
RADIOLABELLING INFORMATION (if applicable)
- Radiochemical purity: N/A
- Specific activity: N/A
- Locations of the label: N/A
- Expiration date of radiochemical substance: N/A
STABILITY AND STORAGE CONDITIONS OF TEST MATERIAL
- Storage condition of test material: +15 to +25ºC purged with nitrogen
- Stability of formulation under test conditions: stable - confirmed at 0.8 and 250 mg/mL.
- Solubility and stability of the test substance in the diet: N/A
- Reactivity of the test substance with the solvent/vehicle of the cell culture medium: N/A
TREATMENT OF TEST MATERIAL PRIOR TO TESTING
- Treatment of test material prior to testing: Based on results of validation study (Study No. G17456), test item formulations prepared at 0.8 and 250 mg/mL in the vehicle (Corn oil) were stable and resuspendable in the vehicle for 48 hours when stored at room temperature at both the concentrations.
- Preliminary purification step (if any): N/A
- Final dilution of a dissolved solid, stock liquid or gel: N/A
- Final preparation of a solid: N/A
FORM AS APPLIED IN THE TEST (if different from that of starting material) N/A
OTHER SPECIFICS: N/A
Test animals
- Species:
- rabbit
- Strain:
- New Zealand White
- Details on test animals or test system and environmental conditions:
- . TEST ANIMALS
- Source: Liveon Biolabs Pvt. Ltd, Plot No.46 and 47, Water Tank Road, II Phase, KIADB Industrial Area, Antharasanahalli Kasaba Hobli, Tumkur District, Pin-572 106, Karnataka, India
- Females (if applicable) nulliparous and non-pregnant: yes
- Age at study initiation: 7 months
- Weight at study initiation: Females: 3.207 - 3.244 kg.
- Fasting period before study: no
- 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 Width 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). .
- Water (e.g. ad libitum): ad libitum in polycarbonate bottles with stainless steel sipper tubes
- Acclimation period: 5 days prior to the commencement of treatment.
DETAILS OF FOOD AND WATER QUALITY: Rabbit feed manufactured by Special Diets Services, P.O Box 705, Witham, Essex, CM8 3AD, England (Batch No.3439) was provided ad libitum in stainless steel feed hoppers to rabbitse. Deep bore-well water passed through activated charcoal filter and exposed to UV rays in Aquaguard water filter-cum-purifier (Eureka Forbes Ltd, Mumbai, India) was provided ad libitum in polycarbonate bottles with stainless steel sipper tubes to rabbits.
ENVIRONMENTAL CONDITIONS
- Temperature (°C): 19 to 21 ºC
- Humidity (%): 64 to 65 %
- Air changes (per hr): 12 - 15 air changes/hour.
- Photoperiod (hrs dark / hrs light): 12 hours light and 12 hours dark cycle.
IN-LIFE DATES: From: 29 December 2018 To 12 February 2019
Administration / exposure
- Route of administration:
- oral: gavage
- Vehicle:
- corn oil
- Details on exposure:
- PREPARATION OF DOSING SOLUTIONS:
Dose formulations were prepared prior to treatment and used within the stability period of 48 hours.
VEHICLE - Justification for use and choice of vehicle (if other than water): Cornoil
- Concentration in vehicle: not specified
- Amount of vehicle (if gavage): 1 mL/kg body weight
- Lot/batch no. (if required): MKCF8882
- Purity: not stated - Analytical verification of doses or concentrations:
- yes
- Details on analytical verification of doses or concentrations:
- The method for determination of the test item concentration in dose formulation with the vehicle (corn oil) was successfully validated for specificity, linearity and range, LOD, LOQ, accuracy and precision at a claimed concentration of 0.833 and 250.50 mg/mL. The test item was observed to form homogenous suspension in the vehicle and found to be stable and re-suspendable in the vehicle at 0.833 and 250.50 mg/mL up to 48 hours, when stored at room temperature
- Details on mating procedure:
- During the mating period, females were cohabited randomly with males in a 1:1 ratio. in rabbit cages (approximate size: Length 65 cm x Width 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). After confirmation of mating by visual examination, the Gestation Day 0 (GD 0) was recorded for each individual rabbit.
- Duration of treatment / exposure:
- GD 6 to GD 28
- Frequency of treatment:
- Daily
- Duration of test:
- 23 days
Doses / concentrationsopen allclose all
- Dose / conc.:
- 0 mg/kg bw/day (nominal)
- Remarks:
- Vehicle Control
- Dose / conc.:
- 15 mg/kg bw/day (nominal)
- Remarks:
- Low dose
- Dose / conc.:
- 50 mg/kg bw/day (nominal)
- Remarks:
- Mid dose
- Dose / conc.:
- 60 mg/kg bw/day (nominal)
- Remarks:
- High dose
- No. of animals per sex per dose:
- 23
- Control animals:
- yes, concurrent vehicle
- Details on study design:
- - Dose selection rationale:
A preliminary dose range finding study (DRF) in pregnant female New Zealand White rabbits was carried out using 6 rabbits per group with the test item by oral gavage at a dose volume of 2 mL/kg body weight at 50, 150 and 300 mg/kg bw/day along with the concurrent vehicle control.
Based on the findings, 0, 15, 30 and 60 mg/kg/day dose levels at a dose volume of 1 mL/kg body weight were selected for the definitive study.
- Rationale for animal assignment (if not random): N/A - Other:
The test item formulations or vehicle was administered daily by oral gavage approximately the same time each day (varying by ± 2 hours). The dosing was performed using a suction catheter attached to a plastic disposable syringe from GD 6 to GD 28 of presumed gestation. Dose formulation was administered at 1 mL/kg body weight, with actual volume administered based on the most recent body weight.Dose formulations were continuously stirred during dose administrations. The animals in the vehicle control (G1) group were handled and administered vehicle in an identical manner to the treatment groups.
Examinations
- Maternal examinations:
- CAGE SIDE OBSERVATIONS: Not Stated
- Time schedule:
- Cage side observations checked in table [No.?] were included.
DETAILED CLINICAL OBSERVATIONS: Yes
- Time schedule: 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).
BODY WEIGHT: Yes - Time schedule for examinations: 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.
FOOD CONSUMPTION AND COMPOUND INTAKE (if feeding study): Yes
- Food consumption for each animal determined and mean daily diet consumption calculated as g food/kg body weight/day: Yes - Compound intake calculated as time-weighted averages from the consumption and body weight gain data: No
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.
WATER CONSUMPTION AND COMPOUND INTAKE (if drinking water study): Not Stated
- Time schedule for examinations: Not Stated POST-MORTEM EXAMINATIONS: Yes - Sacrifice on gestation day # GD 29
- Organs examined: Yes, external and visceral organs
OTHER: The following data were recorded.
* Pregnancy status
* Gravid Uterine weight (from all rabbits subjected to caesarean section)
* Number of corpora lutea
* Number of implantation sites
* Number of early resorptions
* Number of late resorptions
* Gross evaluation of placenta - 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: Yes, gross evaluation of placenta, pregnancy status - Fetal examinations:
- - External examinations: Yes:
- Soft tissue examinations: Yes:
- Skeletal examinations: Yes:
- Head examinations: Yes:
- Other: The following litter data were recorded:
* Total number of fetuses
* Number of live fetuses
* Number of dead fetuses
* Individual fetal body weight
* Fetus sex - 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/deaths, pre-implantation and post-implantation loss, external, soft tissue and skeletal observations for variations were analyzed using Kruskal Wallis test for group comparison. 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.
Statistically significant differences (p<0.05) were designated as * - Indices:
- n/a
- Historical control data:
- Yes
Results and discussion
Results: maternal animals
General toxicity (maternal animals)
- Clinical signs:
- no effects observed
- Description (incidence and severity):
- There was a total of four abortions observed – one at each dose group. viz, one each in vehicle control and at 15 mg/kg/day on GD 26, one at 30 mg/kg/day on GD 27 and one at 60 mg/kg/day on GD 23. Rabbits being sensitive animals, occurance of abortions are considered incidental.
- Dermal irritation (if dermal study):
- not examined
- Mortality:
- no mortality observed
- Body weight and weight changes:
- no effects observed
- Description (incidence and severity):
- The mean maternal body weights, body weight gain and adjusted body weights during the different periods of gestation (GD 0-6; GD 6-29; GD 0-29) of the treated rabbits were statistically comparable to the vehicle control group at all the doses tested.
- Food consumption and compound intake (if feeding study):
- effects observed, non-treatment-related
- Description (incidence and severity):
- Compared to the vehicle control group, there was no change in food consumption of rabbits dosed at 15 mg/kg/day. There was a significant decrease (23 to 33%) in food consumption during initial stage of gestation (GD 6-9) at 30 mg/kg/day. The significant reduction (21 to 33%) in food consumption was observed during GD 6-9, 9-12, 12-15, 18-21, 24-27, 27-29, 6-29 and 0-29 at 60 mg/kg/day.
The reduction in food consumption at 30 mg/kg/day was observed during initial stage and hence was not considered adverse as the food consumption during treatment period was comparable to control group. Also the reduction at 60 mg/kg/day was not of any toxicological significance as there was no concomittent reduction in maternal body weights. - Food efficiency:
- not specified
- Water consumption and compound intake (if drinking water study):
- not specified
- 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:
- no effects observed
- Gross pathological findings:
- no effects observed
- Description (incidence and severity):
- There were no gross pathological findings in any of the treated groups
- Neuropathological findings:
- not examined
- Histopathological findings: non-neoplastic:
- not examined
- Histopathological findings: neoplastic:
- not examined
- Other effects:
- not specified
Maternal developmental toxicity
- Number of abortions:
- effects observed, non-treatment-related
- Description (incidence and severity):
- Incidental abortions were observed in each of the, vehicle control, low, mid and high dose groups. There was a total of four abortions observed – one at each dose group. viz, one each in vehicle control and at 15 mg/kg/day on GD 26, one at 30 mg/kg/day on GD 27 and one at 60 mg/kg/day on GD 23. Rabbits being sensitive animals, occurance of abortions are considered incidental.
- Pre- and post-implantation loss:
- no effects observed
- Total litter losses by resorption:
- no effects observed
- Early or late resorptions:
- no effects observed
- Dead fetuses:
- no effects observed
- Changes in pregnancy duration:
- no effects observed
- Changes in number of pregnant:
- no effects observed
- Other effects:
- not specified
Effect levels (maternal animals)
- Key result
- Dose descriptor:
- NOEL
- Effect level:
- 60 mg/kg bw/day (actual dose received)
- Based on:
- test mat.
- Remarks on result:
- not determinable due to absence of adverse toxic effects
Maternal abnormalities
- Key result
- Abnormalities:
- no effects observed
Results (fetuses)
- Fetal body weight changes:
- no effects observed
- Reduction in number of live offspring:
- no effects observed
- Changes in sex ratio:
- no effects observed
- Changes in litter size and weights:
- no effects observed
- Changes in postnatal survival:
- no effects observed
- External malformations:
- no effects observed
- Skeletal malformations:
- no effects observed
- Visceral malformations:
- no effects observed
- Other effects:
- not specified
Effect levels (fetuses)
- Key result
- Dose descriptor:
- NOEL
- Effect level:
- 60 mg/kg bw/day (actual dose received)
- Based on:
- test mat.
- Sex:
- male/female
- Remarks on result:
- not determinable due to absence of adverse toxic effects
Fetal abnormalities
- Key result
- Abnormalities:
- no effects observed
Overall developmental toxicity
- Key result
- Developmental effects observed:
- no
Any other information on results incl. tables
Table 2. Summarized Details of Necropsy
Parameters |
GD 6 to 28 (total 23 days) |
||||
Group No. & |
G1 |
G2 |
G3 |
G4 |
|
Dose (mg/kg/day) |
0 |
15 |
30 |
60 |
|
Total No. of rabbits / group |
23 |
23 |
23 |
23 |
|
Caesarean section (day of presumed gestation) |
29 |
||||
Number of rabbits aborted |
1 |
1 |
1 |
1 |
|
Number of rabbits sacrificed at caesarean section |
22 |
22 |
22 |
22 |
|
Number of rabbits non-pregnant at caesarean section |
1 |
3 |
2 |
2 |
|
Number of pregnant rabbits examined at caesarean section. |
21 |
19 |
20 |
20 |
|
Number of litters examined |
21 |
19 |
20 |
20 |
|
Total number of fetuses |
123 |
110 |
125 |
100 |
|
Number fetuses evaluated |
|||||
External, visceral and skeletal |
123 |
110 |
125 |
100 |
|
Number of fetus for decapitation |
57 |
51 |
57 |
45 |
|
Number of Entire fetuses |
66 |
59 |
68 |
55 |
Table 3. Summary of Clinical Signs and Mortality
Observation from Day 0- 29 |
G1 |
G2 |
G3 |
G4 |
0mg/kg/day |
15mg/kg/day |
30mg/kg/day |
60mg/kg/day |
|
Normal |
23 |
23 |
23 |
23 |
Killed - humane |
1 |
1 |
1 |
1 |
Killed – terminal kill |
22 |
22 |
22 |
22 |
Abortion |
1 |
1 |
1 |
1 |
Table 4. Mean Maternal Body Weight of Pregnant Rabbits
Day(s) Relative to Mating |
G1 |
G2 |
G3 |
G4 |
0mg/kg/day |
15mg/kg/day |
30mg/kg/day |
60mg/kg/day |
|
0 |
3.1839 |
3.2551 |
3.2157 |
3.1727 |
3 |
3.2278 |
3.2565 |
3.2214 |
3.1932 |
6 |
3.2397 |
3.2609 |
3.2450 |
3.2031 |
9 |
3.2364 |
3.2367 |
3.2246 |
3.1645 |
12 |
3.2203 |
3.2613 |
3.2137 |
3.1712 |
15 |
3.2463 |
3.2613 |
3.2394 |
3.1870 |
18 |
3.2881 |
3.2702 |
3.2400 |
3.2124 |
21 |
3.2652 |
3.2697 |
3.2312 |
3.2279 |
24 |
3.2688 |
3.2923 |
3.2361 |
3.2464 |
27 |
3.2667 |
3.2967 |
3.2399 |
3.2464 |
29 |
3.2898 |
3.3183 |
3.2701 |
3.2703 |
Table 5. Mean Maternal Body Weight Gain of Pregnant Rabbits
Day(s) Relative to Mating |
G1 |
G2 |
G3 |
G4 |
|
0mg/kg/day |
15mg/kg/day |
30mg/kg/day |
60mg/kg/day |
||
Absolute Weight Gain (kg) |
0-3[a] |
0.0604 |
0.0655 |
0.0461 |
0.0577 |
3-6[a] |
0.0120 |
0.0044 |
0.0236 |
0.0577 |
|
6®9[a] |
-0.0033 |
-0.0243 |
-0.0204 |
-0.0386 |
|
9-12[a] |
-0.0161 |
0.0246 |
-0.0109 |
0.0386 |
|
12-15[a] |
0.0260 |
0.0008 |
0.0258 |
0.0159 |
|
15-18[a] |
0.0418 |
0.0081 |
0.0005 |
0.0253 |
|
18-21[a] |
-0.0229 |
-0.0005 |
-0.0088 |
0.01155 |
|
21-24[a] |
0.0036 |
0.0226 |
0.0049 |
0.0185 |
|
24-27[a] |
-0.0021 |
0.0044 |
0.0038 |
0.0063 |
|
27-29[a] |
0.0231 |
0.0216 |
0.0302 |
0.0176 |
|
Absolute Weight Gain (kg) |
0-6[a] |
0.0559 |
0.0058 |
0.0293 |
0.0304 |
6-29[a] |
0.0501 |
0.0573 |
0.0251 |
0.0672 |
|
0-29[a] |
0.1060 |
0.0632 |
0.0544 |
0.0976 |
|
Adjusted Bodyweight (kg) |
[a] |
2.9490 |
2.9851 |
2.9145 |
2.9708 |
Adjusted Weight Gain (kg) |
[a] |
-0.2908 |
-0.2759 |
-0.3304 |
-0.2323 |
Table 6. Summary of Total Food Consumption of Pregnant Rabbits
Day(s) Relative to Mating |
G1 |
G2 |
G3 |
G4 |
0mg/kg/day |
15mg/kg/day |
30mg/kg/day |
60mg/kg/day |
|
0-3 |
352 |
339.12 |
325.11 |
339.43 |
3-6 |
359.95 |
343.88 |
363.06 |
349.58 |
6-9 |
343.10 |
284.01 |
261.62* |
219.70* |
9-12 |
313.12 |
301.31 |
267.23 |
209.51* |
12-15 |
289.60 |
286.43 |
253.20 |
195.73* |
15-18 |
277.97 |
242.42 |
241.84 |
222.53 |
18 -21 |
269.25 |
269.20 |
254.87 |
212.28* |
21-24 |
244.97 |
236.44 |
214.13 |
210.16 |
24 - 27 |
223.53 |
250.10 |
194.14 |
173.13* |
27- 29 |
183.45 |
193.56 |
176.08 |
130.10* |
0 - 3[a] |
0.0604 |
0.0655 |
0.0461 |
0.0577 |
Anova & Dunnett(Log): * = p < 0.05
Table 7. Mean Food Consumption of Pregnant Rabbits
Day(s) Relative to Mating |
G1 |
G2 |
G3 |
G4 |
0mg/kg/day |
15mg/kg/day |
30mg/kg/day |
60mg/kg/day |
|
0 - 3 |
117.49 |
113.04 |
108.37 |
113.14 |
3 - 6 |
119.98 |
114.63 |
121.02 |
116.53 |
6 - 9 |
114.37 |
94.67 |
87.20* |
73.23* |
9 - 12 |
104.37 |
100.44 |
89.08 |
69.84* |
12 -15 |
96.53 |
95.48 |
84.40 |
65.24* |
15 - 18 |
92.66 |
80.81 |
80.61 |
74.18 |
18 - 21 |
89.75 |
89.73 |
84.96 |
70.76* |
21 - 24 |
81.66 |
78.81 |
71.38 |
70.13 |
24 - 27 |
74.51 |
83.37 |
64.71 |
57.71* |
27 - 29 |
74.51 |
83.37 |
88.04 |
65.05* |
0 - 6 |
118.74 |
113.83 |
114.69 |
114.83 |
6 - 29 |
93.26 |
89.72 |
81.00* |
68.41* |
0 - 29 |
98.53 |
94.71 |
87.97 |
78.01* |
Anova & Dunnett(Log): * = p < 0.05
Table 8. Summary of Gross Necropsy Findings
Parameter |
Group No. & |
G1 |
G2 |
G3 |
G4 |
Dose (mg/kg/day) |
0 |
15 |
30 |
60 |
|
Total No. of rabbits / group |
23 |
23 |
23 |
23 |
|
Number of dead during treatment |
0 |
0 |
0 |
0 |
|
Number of moribund sacrifice |
0 |
0 |
0 |
0 |
|
Number of terminally sacrificed |
23 |
23 |
23 |
23 |
|
Number of examined for gross pathology. |
23 |
23 |
23 |
23 |
|
Number showing gross pathology |
Showing external pathology |
0 |
0 |
0 |
0 |
Showing visceral organ pathology |
0 |
0 |
0 |
0 |
Table 9. Summary of Maternal Data
Parameter |
GD |
G1 |
G2 |
G3 |
G4 |
0mg/kg/day |
15mg/kg/day |
30mg/kg/day |
60mg/kg/day |
||
Pregnant |
GD29 |
21 |
19 |
20 |
20 |
Gravid Uterus (g) |
GD29 [a] |
340.9 |
333.2 |
355.6 |
299.5 |
Number of Corpora Lutea |
GD29 [k] |
7.4 |
7.7 |
8.3 |
7.5 |
No. of Implantation |
GD29 [k] |
6.3 |
6.2 |
6.7 |
5.9 |
No. of Early Deaths |
GD29 [k] |
0.1 |
0.3 |
0.2 |
0.8 |
No. of Late Deaths |
GD29 [k] |
0.3 |
0.2 |
0.2 |
0.4 |
Pre-implantation loss/Animal |
GD29 [k] |
1.14 |
1.53 |
1.65 |
1.60 |
% Pre-implantation loss |
GD29 [k] |
15.7 |
20.3 |
19.8 |
22.7 |
Post-implantation loss/Animal |
GD29 [k] |
0.43 |
0.42 |
0.40 |
0.90 |
% Post-implantation loss |
GD29 [k] |
6.2 |
6.5 |
5.5 |
17.7 |
Resorptions |
GD29 [f] |
21 |
19 |
20 |
20 |
[a] - Anova & Dunnett(Log)
[k] - Kruskal-Wallis & Wilcoxon
[f] - Chi-Squared & Fisher's Exact
Table 10. Summary of Litter Data
Parameter |
GD |
G1 |
G2 |
G3 |
G4 |
0mg/kg/day |
15mg/kg/day |
30mg/kg/day |
60mg/kg/day |
||
Pregnant |
GD29 |
21 |
19 |
20 |
20 |
Total No. of Fetuses |
GD29 [a] |
5.9 |
5.8 |
6.3 |
5.0 |
Dead |
[a] |
0 |
0 |
0 |
0 |
Live Male |
sum |
67 |
58 |
59 |
50 |
Mean Fetal Weight (M) (g) |
GD29 [c] |
38.64 |
41.16 |
38.59 |
39.02 |
Live Female |
sum |
56 |
52 |
66 |
50 |
Mean Fetal Weight (F) (g) |
GD29 [c1] |
38.95 |
40.32 |
37.86 |
40.85 |
Live both |
sum |
123 |
110 |
125 |
100 |
Mean Fetal Weight (both) (g) |
GD29 [c2] |
38.96 |
40.37 |
38.34 |
40.09 |
[a] ‑ Anova & Dunnett(Log)
[c] ‑ Ancova/Anova & Dunnett; {Covariate(s): Number of Live Male Fetuses}
[c1] ‑ Ancova/Anova & Dunnett; Covariate(s): Number of Live Female Fetuses}
[c2] ‑ Ancova/Anova & Dunnett; {Covariate(s): Number of Live Fetuses}
Table 11. Summary of Fetal External, Visceral and Skeletal Observations
Group |
G1 |
G2 |
G3 |
G4 |
||
Dose |
0mg/kg/day |
15mg/kg/day |
30mg/kg/day |
60mg/kg/day |
||
No. of Fetuses examined |
123 |
110 |
125 |
100 |
||
No. of Litters Evaluated |
21 |
19 |
20 |
20 |
||
Exam Type: External |
|
|
|
|
||
Body
|
Umbilicus, Hernia - Anomaly |
Fetuses N(%)
Litters N(%) |
0(0.0)
0(0.0) |
0(0.0)
0(0.0) |
0(0.0)
0(0.0) |
0(0.0)
0(0.0) |
Exam Type: Fresh Visceral-Body Only |
|
|
|
|
||
Abdomen
|
Gallbladder, Hyperplastic - Anomaly |
Fetuses N(%)
Litters N(%) |
1(1.8)
1(4.8) |
0(0.0)
0(0.0) |
0(0.0)
0(0.0) |
1(1.0)
1(5.0) |
Gallbladder, Bilobed gallbladder – Anomaly |
Fetuses N(%)
Litters N(%) |
0(0.0)
0(0.0) |
2(1.8)
2(10.5) |
0(0.0)
0(0.0) |
0(0.0)
0(0.0) |
|
Gallbladder, Hypoplastic - Anomaly |
Fetuses N(%)
Litters N(%) |
9(7.3)
5(23.8) |
8(7.3)
6(31.6) |
4(3.2)
3(15.0) |
1(1.0)
1(5.0) |
|
Exam Type: Skeletal - Body |
|
|
|
|
||
Hindlimbs: |
Metatarsal, middle phalange-4, Delayed skeletal ossification - Variation |
Fetuses N(%)
Litters N(%) |
0(0.0)
0(0.0) |
2(3.9)
1(5.3) |
0(0.0)
0(0.0) |
0(0.0)
0(0.0) |
Lumbar vertebrae
|
8th lumbar centrum and arch, Extra - Anomaly |
Fetuses N(%)
Litters N(%) |
8(14.0)
4(19.0) |
3(5.9)
3(15.8) |
4(7.0)
4(20.0) |
4(8.9)
2(11.1) |
Ribs
|
14th rib, Left, Rudimentary - Anomaly |
Fetuses N(%)
Litters N(%) |
1(1.8)
1(4.8) |
0(0.0)
0(0.0) |
0(0.0)
0(0.0) |
0(0.0)
0(0.0) |
13th rib, Right, Accessory - Anomaly |
Fetuses N(%)
Litters N(%) |
0(0.0)
0(0.0) |
2(3.9)
2(10.5) |
1(1.8)
1(5.0) |
1(2.2)
1(5.6) |
|
13th rib, Right, Rudimentary - Anomaly |
Fetuses N(%)
Litters N(%) |
0(0.0)
0(0.0) |
1(2.0)
1(5.3) |
1(1.8)
1(5.0) |
1(2.2)
1(5.6) |
|
13th rib, Right, Rudimentary Float - Anomaly |
Fetuses N(%)
Litters N(%) |
0(0.0)
0(0.0) |
1(2.0)
1(5.3) |
0(0.0)
0(0.0) |
0(0.0)
0(0.0) |
|
13th rib, Right, Extra - Anomaly |
Fetuses N(%)
Litters N(%) |
1(1.8)
1(4.8) |
0(0.0)
0(0.0) |
0(0.0)
0(0.0) |
0(0.0)
1(5.6) |
|
13th rib, Left, Accessory - Anomaly |
Fetuses N(%)
Litters N(%) |
0(0.0)
0(0.0) |
0(0.0)
0(0.0) |
0(0.0)
0(0.0) |
0(0.0)
0(0.0) |
|
13th rib, Left, Accessory Float - Anomaly |
Fetuses N(%)
Litters N(%) |
1(1.8)
1(4.8) |
0(0.0)
2(10.5) |
0(0.0)
0(0.0) |
0(0.0)
0(0.0) |
|
13th rib, Left, Rudimentary - Anomaly |
Fetuses N(%)
Litters N(%) |
0(0.0)
0(0.0) |
0(0.0)
0(0.0) |
0(0.0)
0(0.0) |
0(0.0)
0(0.0) |
|
13th rib, Left, Rudimentary Float - Anomaly |
Fetuses N(%)
Litters N(%) |
0(0.0)
0(0.0) |
1(2.0)
1(5.3) |
1(1.8)
1(5.0) |
0(0.0)
0(0.0) |
|
13th rib, Left, Extra - Anomaly |
Fetuses N(%)
Litters N(%) |
5(8.8)
3(14.3) |
3(5.9)
3(15.8) |
1(1.8)
1(5.0) |
1(2.2)
1(5.6) |
|
13th rib, Bilateral, Accessory Float - Anomaly |
Fetuses N(%)
Litters N(%) |
0(0.0)
0(0.0) |
0(0.0)
0(0.0) |
0(0.0)
0(0.0) |
1(2.2)
1(5.6) |
|
13th rib, Bilateral, Rudimentary - Anomaly |
Fetuses N(%)
Litters N(%) |
2(3.5)
2(9.5) |
0(0.0)
0(0.0) |
2(3.5)
2(10.0) |
1(2.2)
1(5.6) |
|
13th rib, Bilateral, Rudimentary Float - Anomaly |
Fetuses N(%)
Litters N(%) |
0(0.0)
0(0.0) |
1(2.0)
1(5.3) |
0(0.0)
0(0.0) |
0(0.0)
0(0.0) |
|
13th rib, Bilateral, Extra - Anomaly |
Fetuses N(%)
Litters N(%) |
9(15.8)
5(23.8) |
3(5.9)
3(15.8) |
2(3.5)
2(10.0) |
4(8.9)
3(16.7) |
|
Sternebrae
|
4th & 5th sternebrae, Fused - Anomaly |
Fetuses N(%)
Litters N(%) |
1(1.8)
1(4.8) |
0(0.0)
0(0.0) |
0(0.0)
0(0.0) |
0(0.0)
0(0.0) |
6th sternebra, Hypoplastic - Anomaly |
Fetuses N(%)
Litters N(%) |
1(1.8)
1(4.8) |
3(5.9)
3(15.8) |
1(1.8)
1(5.0) |
4(8.9)
3(16.7) |
|
6th sternebra, Incomplete ossification - Variation |
Fetuses N(%)
Litters N(%) |
7(12.3)
6(28.6) |
4(7.8)
3(15.8) |
6(10.5)
4(20.0) |
1(2.2)
1(5.6) |
|
6th sternebra, Poor ossification - Variation |
Fetuses N(%)
Litters N(%) |
6(28.6)
0(0.0) |
3(15.8)
2(3.9) |
4(20.0)
0(0.0) |
0(0.0)
1(5.6) |
|
6th sternebra, Delayed skeletal ossification - Variation |
Fetuses N(%)
Litters N(%) |
1(1.5)
1(4.8) |
0(0.0)
0(0.0) |
1(1.5)
1(5) |
0(0.0)
0(0.0) |
|
6th sternebra, Incomplete ossification - Variation |
Fetuses N(%)
Litters N(%) |
1(4.8)
3(4.5) |
0(0.0)
5(8.5) |
1(5.0)
4(5.9) |
0(0.0)
2(3.6) |
|
5th sternebra, Hypoplastic - Anomaly |
Fetuses N(%)
Litters N(%) |
3(14.3)
14(21.2) |
4(21.1)
15(25.4) |
3(15.0)
17(25.0) |
2(10.0)
8(14.5) |
|
5th sternebra, Delayed skeletal ossification - Variation |
Fetuses N(%)
Litters N(%) |
14(21.2)
9(42.9) |
15(25.4)
12(63.2) |
17(25.0)
11(55.0) |
8(21.1)
15(25.4) |
|
5th sternebra, Poor ossification - Variation |
Fetuses N(%)
Litters N(%) |
6(28.6)
2(3.0) |
9(15.3)*
7(36.8) |
3(4.4)
3(15.0) |
0(0.0)
0(0.0) |
|
5th sternebra, Incomplete ossification - Variation |
Fetuses N(%)
Litters N(%) |
16(24.2)
9(42.9) |
15(25.4)
12(63.2) |
19(27.9)
11(55.0) |
18(32.7)
15(75.0) |
|
4th sternebra, Delayed skeletal ossification - Variation |
Fetuses N(%)
Litters N(%) |
0(0.0)
0(0.0) |
0(0.0)
0(0.0) |
0(0.0)
0(0.0) |
1(1.8)
1(1.5) |
|
2nd sternebra, Hypoplastic - Anomaly |
Fetuses N(%)
Litters N(%) |
1(1.5)
1(4.8) |
0(0.0)
0(0.0) |
0(0.0)
0(0.0) |
0(0.0)
0(0.0) |
|
2nd sternebra, Incomplete ossification - Variation |
Fetuses N(%)
Litters N(%) |
4(6.1)
3(14.3) |
4(6.8)
2(10.5) |
3(4.4)
3(15.0) |
2(3.6)
2(10) |
|
Forelimbs |
Metacarpal, middle phalange-5, Delayed skeletal ossification - Variation |
Fetuses N(%)
Litters N(%) |
5(7.6)
3(14.3) |
4(6.8)
2(21.1) |
3(4.4)
3(15.0) |
3(5.5)
2(10.0) |
Carpal bone, Right, Bent, Slight - Anomaly |
Fetuses N(%)
Litters N(%) |
1(1.5)
1(4.8) |
0(0.0)
0(0.0) |
0(0.0)
0(0.0) |
0(0.0)
0(0.0) |
|
Skull |
Parietal, Extra suture - Variation |
Fetuses N(%)
Litters N(%) |
1(1.5)
1(4.8) |
0(0.0)
0(0.0) |
0(0.0)
0(0.0) |
0(0.0)
0(0.0) |
Fontanelle, Enlarged - Variation |
Fetuses N(%)
Litters N(%) |
0(0.0)
0(0.0) |
0(0.0)
0(0.0) |
0(0.0)
0(0.0) |
1(1.8)
1(5.0) |
Applicant's summary and conclusion
- Conclusions:
- Exposure to the Amyl Cinnamic Aldehyde up to 60 mg/kg bw/day caused no evident toxicity related to clinical signs, body weights, food consumption or gross necropsy findings at any of the doses tested except for one incidental abortion in all treatment groups including vehicle control. The maternal and litter data parameters were unaffected, fetal external, visceral and skeletal examination revealed no signs of teratogenicity up to the highest tested dose of 60 mg/kg/day.
In conclusion, based on the above findings, under the test conditions employed in the study, it was concluded that No - Observed - Effect Level (NOEL) for: Maternal toxicity and fetal developmental toxicity is 60 mg/kg/day. Therefore, the substance does not meet the criteria for classification according to Regulation (EC) No 1272/2008 (CLP). - Executive summary:
OECD 414 - (2019): Amyl Cinnamic Aldehyde 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. 92 mated female rabbits were assigned to four groups. Each group consisted of 23 mated rabbits (G1: vehicle control, G2: low dose, G3: mid dose and G4: high dose). Day 0 of gestation for each individual female rabbit in the study was considered as the day on which mating had occurred. Test item in vehicle (Corn oil) was administered at 0, 15, 30 and 60 mg/kg/day at the dose volume of 1mL/kg body weight. The control group received the vehicle only.
The data of maternal and litter parameters were analysed and presented only for pregnant rabbits at caesarean section. There were no clinical signs or mortalities observed at any of the doses tested during the study period. However, there was a total of four abortions observed – one at each dose group viz, one each in vehicle control and at 15 mg/kg/day on GD 26, one at 30 mg/kg/day on GD 27 and one at 60 mg/kg/day on GD 24. Rabbits being sensitive animals, occurance of abortions are considered incidental.
The mean maternal body weights, body weight gain and adjusted body weights during the different periods of gestation (GD 0-6; GD 6-29; GD 0-29) of the treated rabbits were statistically comparable to the vehicle control group at all the doses tested.
Compared to the vehicle control group, there was no change in food consumption of rabbits dosed at 15 mg/kg/day. There was a significant decrease (24%) in food consumption during initial stage of gestation (GD 6-9) at 30 mg/kg/day. The significant reduction (21 to 36%) in food consumption was observed during GD 6-9, 9-12, 12-15, 18-21, 24-27, 27-29, 6-29 and 0-29 at 60 mg/kg/day. The reduction in food consumption at 30 mg/kg/day was observed during initial stage and hence was not considered adverse as the food consumption during treatment period was comparable to control group. Also the reduction at 60 mg/kg/day was not of any toxicological significance as there was no concomittent reduction in maternal body weights.
The maternal parameters comprising of gravid uterine weight and mean number of corpora lutea, implantations, early and late resorptions, pre and post implantation loss and dams with resorptions were statistically comparable between the vehicle control and rabbits treated at 15, 30 and 60 mg/kg/day. Gross evaluation of placenta did not reveal any findings in any dams at any tested dose levels.
The litter parameters comprising total number of fetuses, mean fetal weight were comparable between the vehicle control group and rabbits treated at all the doses tested.
No test item related major abnormality was observed during external observation of the fetuses at any of the doses. Anomaly of umbilical hernia was observed in one fetus of a litter with 2 fetuses (RBa5031) at 60 mg/kg/day. This was considered as an incidental finding.
There were no test item related major visceral malformations observed in fetuses of dams treated up to 60 mg/kg/day. Anomalies such as gall bladder hypoplastic in vehicle and test item treated groups and hyperplastic gall bladder in control and high dose group, bilobed gall bladder in low dose 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 was consistent with concurrent or historical controls.
There were no test item related skeletal malformations observed in fetuses of dams treated up to 60 mg/kg/day. Variants and anomalies observed across vehicle and test item treated groups were comparable and are consistent with concurrent and historical data.
There were no gross pathological changes at any dose level. External and visceral and skeletal examination of fetuses revealed no signs of teratogenicity.
In conclusion, based on the above findings, under the test conditions employed in the study, it was concluded that No - Observed - Effect Level (NOEL) for: Maternal toxicity and fetal developmental toxicity is 60 mg/kg/day. Therefore, the substance does not meet the criteria for classification according to Regulation (EC) No 1272/2008 (CLP).
criteria for classification according to Regulation (EC) No 1272/2008 (CLP). criteria for classification according to Regulation (EC) No 1272/2008 (CLP).
Information on Registered Substances comes from registration dossiers which have been assigned a registration number. The assignment of a registration number does however not guarantee that the information in the dossier is correct or that the dossier is compliant with Regulation (EC) No 1907/2006 (the REACH Regulation). This information has not been reviewed or verified by the Agency or any other authority. The content is subject to change without prior notice.
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