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EC number: 451-690-9 | CAS number: 86273-46-3
- Life Cycle description
- Uses advised against
- Endpoint summary
- Appearance / physical state / colour
- Melting point / freezing point
- Boiling point
- Density
- Particle size distribution (Granulometry)
- Vapour pressure
- Partition coefficient
- Water solubility
- Solubility in organic solvents / fat solubility
- Surface tension
- Flash point
- Auto flammability
- Flammability
- Explosiveness
- Oxidising properties
- Oxidation reduction potential
- Stability in organic solvents and identity of relevant degradation products
- Storage stability and reactivity towards container material
- Stability: thermal, sunlight, metals
- pH
- Dissociation constant
- Viscosity
- Additional physico-chemical information
- Additional physico-chemical properties of nanomaterials
- Nanomaterial agglomeration / aggregation
- Nanomaterial crystalline phase
- Nanomaterial crystallite and grain size
- Nanomaterial aspect ratio / shape
- Nanomaterial specific surface area
- Nanomaterial Zeta potential
- Nanomaterial surface chemistry
- Nanomaterial dustiness
- Nanomaterial porosity
- Nanomaterial pour density
- Nanomaterial photocatalytic activity
- Nanomaterial radical formation potential
- Nanomaterial catalytic activity
- Endpoint summary
- Stability
- Biodegradation
- Bioaccumulation
- Transport and distribution
- Environmental data
- Additional information on environmental fate and behaviour
- Ecotoxicological Summary
- Aquatic toxicity
- Endpoint summary
- Short-term toxicity to fish
- Long-term toxicity to fish
- Short-term toxicity to aquatic invertebrates
- Long-term toxicity to aquatic invertebrates
- Toxicity to aquatic algae and cyanobacteria
- Toxicity to aquatic plants other than algae
- Toxicity to microorganisms
- Endocrine disrupter testing in aquatic vertebrates – in vivo
- Toxicity to other aquatic organisms
- Sediment toxicity
- Terrestrial toxicity
- Biological effects monitoring
- Biotransformation and kinetics
- Additional ecotoxological information
- Toxicological Summary
- Toxicokinetics, metabolism and distribution
- Acute Toxicity
- Irritation / corrosion
- Sensitisation
- Repeated dose toxicity
- Genetic toxicity
- Carcinogenicity
- Toxicity to reproduction
- Specific investigations
- Exposure related observations in humans
- Toxic effects on livestock and pets
- Additional toxicological data
![](https://echa.europa.eu/o/diss-blank-theme/images/factsheets/A-REACH/factsheet/print_toxicological-information.png)
Endpoint summary
Administrative data
Key value for chemical safety assessment
- Toxic effect type:
- dose-dependent
Effects on fertility
Description of key information
OECD 422 (Combined Repeated Dose Toxicity with Reproduction/ Developmental Toxicity Study in Rats): the no-observed-adverse-effect level (NOAEL) and the no-observed-effect level (NOEL) of 2-(2-Vinyloxyethoxy) ethyl acrylate on the reproduction performance of the parental animals and on the development of pups were estimated to be 400 mg/kg/day under the conditions of this study.
Link to relevant study records
- Endpoint:
- screening for reproductive / developmental toxicity
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Study period:
- Between June 25th 2008 and March 24th 2009
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- other: Study conducted in compliance with agreed protocols, with no or minor deviations from standard test guidelines and/or minor methodological deficiencies, which do not affect the quality of the relevant results.
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 422 (Combined Repeated Dose Toxicity Study with the Reproduction / Developmental Toxicity Screening Test)
- Deviations:
- no
- GLP compliance:
- yes
- Limit test:
- no
- Species:
- rat
- Strain:
- other: Crl:CD(SD)
- Sex:
- male/female
- Details on test animals or test system and environmental conditions:
- TEST ANIMALS
- Source:
Charles River Laboratories Japan, Inc., Atsugi Breeding Center
- Age at study initiation:
The animals were ordered at
4 weeks of age; males and females
8 weeks of age; females
Number of animals ordered and received:
4 weeks of age; 52 males and 12 females were ordered, and 54 males and 13 females were received (males in the main test groups and females in the recovery groups) 8 weeks of age; 50 females were ordered, and 52 females were received (females in the main test groups) Males in the recovery groups were selected from the main test groups on the basis of the mean body weight in each group.
Age of animals at the start of administration:
4 weeks of age; 6 weeks of age for males and females
8 weeks of age; 10 weeks of age for female
- Weight at study initiation:
4 weeks of age; 87 to 106 g for males and 65 to 75 g for females
8 weeks of age; 164 to 199 g for females
- Fasting period:
All animals were fasted from the evening on the day before necropsy,
- Housing:
Type of cages: Metal bracket-type cages (300 W × 410 D × 200 H, mm)
with wire mesh floors.
- Number of animals per cage: Three or less during the quarantine and acclimatization period, one after the group assignment, one male and one female during mating period, and one litter after parturition.
- Use of restrainers for preventing ingestion (if dermal):
Not applicable
- Diet:
γ-ray irradiated pellet diet, CRF-1 Animals, had free access to the diet using metal feeders. Each lot of the diet used (lot nos. 080305 and 080509) was analyzed for chemical and bacterial contaminants that might affect the study. The analyses were performed at Japan Food Research Laboratories (Certificate of Analysis No. 108031936-001) or Eurofins Scientific Japan K.K. (Certificate of Analysis No. AR-08-JP-000056-01) for chemical contaminants, and at the diet manufacturer for bacterial contaminants.
- Water:
Method of water supply: Animals had free access to water using an automatic watering system or water bottles.
Analysis for contaminants: Drinking water was analyzed for contaminants that might affect the study. The analysis was conducted on the water
samples collected from the end of the same piping system as that in the animal room (room no. 301) on July 1, 2008, October 1, 2008 and January 7, 2009. The analyses were performed at Nihon Eisei Co., Ltd. and the data were supplied. The contaminants assayed and the limits of acceptable values were in compliance with those prescribed in the Standard Operating Procedure of Safety Research Institute for Chemical Compounds Co., Ltd.
- Acclimation period:
For 13 days
ENVIRONMENTAL CONDITIONS
- Temperature (°C):
21 to 25ºC,
- Humidity (%):
43 to 60%)
- Air changes (per hr):
10 to 15 times/hour
- Photoperiod (hrs dark / hrs light):
Artificial lighting for 12 hours (from 8:00 to 20:00)
IN-LIFE DATES:
From day 1 of administration to the day of necropsy (the day
after day 91 of administration). - Route of administration:
- oral: gavage
- Type of inhalation exposure (if applicable):
- other: Not applicable
- Vehicle:
- other: corn oil
- Details on exposure:
- PREPARATION OF DOSING SOLUTIONS:
Dose formulation and chemical analysis
Dose formulation method: The test substance accurately weighed was added to the vehicle, which was well mixed with a stirrer to prepare a dose formulation.
Frequency: At least every 15 days
Storage condition: At room temperature (measured temperature 21 to 25ºC)
Storage location: The test substance storage room of Safety Research Institute for Chemical Compounds Co., Ltd.
Expiry: 15 days after preparation
Safety precautions: A face mask, gloves, protection glasses (goggles) were used.
Remaining dose formulations: The remaining dose formulations were collected as industrial waste to be incinerated.
Stability of dose formulations:
Before the start of administration, dose formulations of the concentrations 10 and 80 mg/mL were analyzed to confirm stability of the test substance in the dose formulations at room temperature for 15 days (day of preparation was defined as Day 0, Appendix 3).
Confirmation of concentration of dose formulations:
Concentrations of the test substance in the dose formulations of all concentrations were confirmed in a total of 3 times; at the first dose formulation, once during the administration period, and at the final dose formulation.
DIET PREPARATION
γ-ray irradiated pellet diet, CRF-1 was used throughout the study period.
- Rate of preparation of diet (frequency):
Not applicable
- Mixing appropriate amounts with (Type of food):
Not applicable
- Storage temperature of food:
No data
VEHICLE
Identity: Corn oil
Lot number: V8A6289 and V8K7807
Manufacturer: Nacalai Tesque, Inc.
Storage condition: At room temperature (measured temperature 21 to 25ºC)
Safety precautions: Nothing specified.
Expiry: 3 years after manufacture - Details on mating procedure:
- M/F ratio per cage:
1/1 (Animals were paired on a 1 male: 1 female basis within each dose group)
- Length of cohabitation:
Up to 14 days
- Proof of pregnancy:
Cage tray-liners were checked each morning for the presence of ejected copulation plugs and each female was examined for the presence of a copulation plug in the vagina. A vaginal smear was prepared for each female and the stage of the oestrous cycle or the presence of sperm was recorded. The presence of sperm within the vaginal smear and/or vaginal plug in situ was taken as positive evidence of mating (Day 0 of gestation)
- After ... days of unsuccessful pairing replacement of first male by another male with proven fertility.:
No data
- Further matings after two unsuccessful attempts:
No data
- After successful mating each pregnant female was caged:
Mated females were housed individually during the period of gestation and lactation.
- Any other deviations from standard protocol:
Not applicable- Analytical verification of doses or concentrations:
- yes
- Duration of treatment / exposure:
- Up to 28 consecutive days for the 400 mg/kg/day dose group and up to 54 consecutive days for the 140 and 50 mg/kg/day dose groups
- Frequency of treatment:
- Daily
- Details on study schedule:
Composition of the test groups and animal numbers in each group are as follows:
Test group Dose level (mg/kg) Concentration(mg/mL) Number of animals (Animal number)
Control group 0 0 12 (101 to 112) 12 (151 to 162)
Low dose group 50 10 12 (201 to 212) 12 (251 to 262)
Mid dose group 140 28 12 (301 to 312) 12 (351 to 362)
High dose group 400 80 12 (401 to 412) 12 (451 to 462)
Control group 0 0 5 (101, 105, 107, 108 and 112) 5 (163 to 167)
High dose group 400 80 5 (403, 404, 405,407 and 409) 5 (463 to 467)
To the control group, only the vehicle was dosed by the same method as the other groups.
- Frequency of administration: Once daily, for consecutive days
- Administration time: Between 9:00 and 14:00 Dams during parturition at the above-mentioned administration time were dosed after the completion of parturition.
- Administration period: Males; 70 days before the start of mating, and subsequent 21 days (a total of 91 days)
Females; During 14 days before the start of mating and mating period until successful copulation. Females showing evidence of copulation were dosed during the duration of gestation and until day 5 after parturition (day 0 of lactation was defined as day 0 after parturition). Females that did not deliver were dosed until day 26 of gestation (a total of 43 to 52 days).
Females in the recovery groups; 91 days, which were the same as males
- Recovery period: 14 days after the end of administration period
- Dose volume: 5 mL/kg. Individual dose volume was calculated from the body weight on the day nearest to the administration day.- Dose / conc.:
- 50 mg/kg bw/day (nominal)
- Dose / conc.:
- 140 mg/kg bw/day (nominal)
- Dose / conc.:
- 400 mg/kg bw/day (nominal)
- No. of animals per sex per dose:
- 10 animals per sex per dose (including control).
- Control animals:
- yes, concurrent vehicle
- Details on study design:
- Dose selection rationale: Dose levels were determined with reference to the 28-day repeated dose oral toxicity (gavage) study1) with the dose levels of 50, 160 and 400 mg/kg. The high dose level was set at 400 mg/kg, with which a tendency to anemia was observed in females, and increasing tendency of reticulocyte counts, hyperkeratosis and ulceration accompanied with chronic inflammation in the stomach, etc. were observed in males and females. The low dose level was set at 50 mg/kg, with which adaptive reactions such as increases in the liver weights, cholesterol or phospholipids were not observed. The middle dose level was set at 140 mg/kg, approximate value obtained by multiplying 50 by the square root of 8.
- Rationale for animal assignment (if not random):
Random.
- Other:
Not applicable- Positive control:
- Not applicable
- Parental animals: Observations and examinations:
- CAGE SIDE OBSERVATIONS:
Yes see atached tables.
- General clinical observation
Animals observed: All animals
Period: From day 1 of administration to the day of necropsy (the day after day 91 of administration). The day of the first administration was defined as day 1 of administration.
Frequency: Twice daily, before and after the administration. Once in the morning on the day of necropsy.
Observation method: Animals were individually observed for mortality, external appearance, behavior, etc. Any abnormal findings were recorded with their duration.
DETAILED CLINICAL OBSERVATIONS:
Yes see atached tables.
- Time schedule:
Animals observed: All animals
Time: Before the start of administration and on days 7, 14, 21, 28, 35, 42, 49, 56, 63, 70, 77, 84 and 91 of administration
BODY WEIGHT:
This method was the same for males
Measurement days: Before administration on Days 1, 3, 5, 7, 10, 14, 21, 28, 35, 42, 49, 56, 63, 70, 77, 84 and 91 of administration and on the day of necropsy.
Measurement method: Animals were weighed with an electronic balance and recorded as the whole number in grams.
Body weight gain and percentage body weight gain were calculated.
Off spring: All live animals were weighed on days 0, 1 and 4 after birth.
FOOD CONSUMPTION:
Animals measured: All animals
Measurement days: Food consumption was measured on the same days as body weight measurement, except on the day of necropsy and during mating period.
Measurement method: Food consumption was measured with an electronic balance and recorded as the whole number in grams. On the day before the start of administration, an adequate amount of diet was measured and set at each cage. The residual amount and the amount supplied were measured on each measurement day.
FOOD EFFICIENCY:
No
WATER CONSUMPTION:
No
HAEMATOLOGY AND CLINICAL CHEMISTRY:
Animals examined: Five animals of each group [except those used for the
functional observational battery at necropsy, 5 animals
were selected from the smallest animal number]
Time: Blood was collected at necropsy
Method of blood collection:
Rats fasted for 16 to 19 hours were anesthetized with
ether and blood samples were collected from the
abdominal aorta.
Examination parameters and methods:
1. Red blood cell count (RBC)
2. Hematocrit (Ht) - Electric resistance method
3. Hemoglobin concentration
4. Mean corpuscular volume (MCV)
5. Mean corpuscular hemoglobin (MCH)
6. Mean corpuscular hemoglobin concentration (MCHC)
7. Reticulocyte count (Reticulocyte) - Brecher’s method (microscopy)
8. Platelet count (Platelet) Electric resistance method
9. White blood cell count (WBC) Electric resistance method
10. Differential count of WBC May-Grünwald-Giemsa staining (microscopy)
11. Prothrombin time (PT) Thromboplastin method
12. Activated partial thromboplastin time (APTT)
Method of blood collection for females: The same as males except for the fasting time for 17 to 19 hours, the parameters measured were the same as
Method of blood collection for the offspring: The same as the main test groups except for the fasting time for 16 to 18 hours, the parameters mwasured were the same as above.
URINALYSIS:
Animals examined: Five animals of each group [the same animals as those used for the functional observational battery]
Time: Week 13 of administration
Method of urine collection: Urine samples were collected using metabolic cages for rats (KN-646, type B-1, Natsume Seisakusyo Co., Ltd.). Urine samples collected immediately after to approximately 3 hours after administration were used for the following parameters 1 to 8, and those collected for approximately 21 hours for parameters 9 and 10. The urine samples were discarded after the completion of examination.
- Time schedule for collection of urine:
urine was collected betwenn the period immediately after dosing and 3 hours after dosing
Examination parameters and methods:
1. pH Test paper method
2. Protein Test paper method
3. Glucose Test paper method
4. Ketone body Test paper method
5. Urobilinogen
6. Bilirubin
7. Occult blood
8. Color - Macroscopic observation
9. Urine volume - Volumetric method
10.Specific gravity
Urinalysis for the offspring
Animals examined: All animals
Time: Week 2 of recovery
Method of urine collection: The same as the main test groups
NEUROBEHAVIOURAL EXAMINATION:
No
Organ weights
Animals weighed: Five animals of each group [the same animals as those used for the hematological examination]. All males for the testes and epididymides.
Time: At necropsy
Measurement method: Absolute weights of the organs described below were measured with an electronic balance. Bilateral organs were measured together. The measurement method was exactly the same for males and females.
Histopathology:
Animals examined: Preparations of all organs and tissues fixed and stored at necropsy were made, and those of 5 animals (the same animals as those used for the hematological examination) in the control and high dose groups were microscopically examined. This process was exactly the smale for male and female animals.
OTHER:
Examination of oestrous cycle
Animals examined: All females
Period: From the day of first administration to the day of successful copulation.
Method: Vaginal smears stained with Giemsa stain were prepared, and stage of oestrous cycle was examined by light microscopy.
Determination: Repetition of each stage (proestrus, estrus, metestrus, and diestrus) of oestrous cycle (one complete cycle comprises of 4 to 6 days) was determined to be normal, and the length (number of days) of oestrous cycle (interval between estrus) was calculated. Continual appearance of diestrus for 7 days or longer was determined to be persistent anestrus, and defined to be abnormal. - Oestrous cyclicity (parental animals):
- Examination of oestrous cycle
Animals examined: All females
Period: From the day of first administration to the day of successful copulation.
Method: Vaginal smears stained with Giemsa stain were prepared, and stage of oestrous cycle was examined by light microscopy.
Determination: Repetition of each stage (proestrus, estrus, metestrus, and diestrus) of oestrous cycle (one complete cycle comprises of 4 to 6 days) was determined to be normal, and the length (number of days) of oestrous cycle (interval between estrus) was calculated. Continual appearance of diestrus for 7 days or longer was determined to be persistent anestrus, and defined to be abnormal. - Sperm parameters (parental animals):
- Parameters examined in [all/P/F1/F2] male parental generations:
[testis weight, epididymis weight, daily sperm production, sperm count in testes, sperm count in epididymides, enumeration of cauda epididymal sperm reserve, sperm motility, sperm morphology, other:] - Litter observations:
- STANDARDISATION OF LITTERS
- Performed on day 4 postpartum:
No
PARAMETERS EXAMINED
The following parameters were examined in offspring:
General clinical observation of offspring
Body weight of offspring
Necropsy of offspring
GROSS EXAMINATION OF DEAD PUPS: - Postmortem examinations (parental animals):
- GROSS NECROPSY / ORGAN WEIGHTS
Animals examined: All animals except those selected for use in the recovery groups
Time: Animals were necropsied on the day after day 91 of administration.
Examination method: Animals were observed for external appearance, and blood was collected under ether anesthesia. They were euthanized by exsanguination and macroscopically observed for all organs and tissues.
Organ weights
Animals weighed: Five animals of each group [the same animals as those used for the hematological examination]. All males for the testes and epididymides.
Time: At necropsy
Measurement method: Absolute weights of the organs described below were measured with an electronic balance. Bilateral organs were measured together. The measurement method was exactly the same for males and females.
Histopathology:
Animals examined: Preparations of all organs and tissues fixed and stored at necropsy were made, and those of 5 animals (the same animals as those used for the hematological examination) in the control and high dose groups were microscopically examined. This process was exactly the smale for male and female animals. - Postmortem examinations (offspring):
- Necropsy
Animals examined: All animals
Time: Animals were necropsied on the day after day 14 of
recovery.
Examination method: The same as the main test groups
Organs and tissues: The same as the main test groups
Organ weights
Animals weighed: All animals
Time: At necropsy
Measurement method: The same as the main test groups
Calculation of relative organ weights:
The same as the main test groups
Organs: The same as the main test groups - Statistics:
- Means and standard deviations were calculated for the results of the following parameters: grip strength, locomotor activity, body weight, body weight gain and percent body weight gain, food consumption, urine volume, hematology, biochemistry, absolute and relative organ weights, length of oestrous cycle, number of corpora lutea, number of implantations and implantation index, number of pups delivered, numbers of live pups and dead pups at delivery, delivery index, live birth index, sex ratio, duration of gestation, number of live pups on day 4 after birth, and viability index, which were analyzed for homogeneity of variances by the Bartlett test. If there was an evidence of homogeneity, the One way analysis of variance (ANOVA) was used, and if there was no evidence of homogeneity, the Kruskal-Wallis test was used. When ANOVA indicated a significant difference, Dunnett’s test was used for comparison with the control group. When the Kruskal-Wallis test indicated a significant difference, the Mann-Whitney U-test was used for comparison with the control group. Body weight of offspring of each sex was analyzed on the litter basis.
As for the findings given two or more different grades in the observation parameters of the detailed clinical observation and the functional observational battery, qualitative parameters of urinalysis, urine specific gravity and histopathology, tendency of each group was analyzed by the Kruskal-Wallis test, and if there was a significant difference, the Mann-Whitney U-test was used for comparison with the control group.
Statistically significant level was set at 5% for comparison with the control group. - Clinical signs:
- effects observed, treatment-related
- Body weight and weight changes:
- no effects observed
- Food consumption and compound intake (if feeding study):
- no effects observed
- Organ weight findings including organ / body weight ratios:
- no effects observed
- Histopathological findings: non-neoplastic:
- effects observed, treatment-related
- Other effects:
- not examined
- Reproductive function: oestrous cycle:
- no effects observed
- Reproductive function: sperm measures:
- no effects observed
- Reproductive performance:
- no effects observed
- Dose descriptor:
- NOEL
- Remarks:
- Reproductive and development toxicity
- Effect level:
- 400 mg/kg bw/day
- Based on:
- test mat.
- Sex:
- male/female
- Basis for effect level:
- other: see 'Remark'
- Clinical signs:
- effects observed, treatment-related
- Mortality / viability:
- mortality observed, treatment-related
- Body weight and weight changes:
- no effects observed
- Sexual maturation:
- not examined
- Organ weight findings including organ / body weight ratios:
- not examined
- Gross pathological findings:
- effects observed, treatment-related
- Histopathological findings:
- not examined
- Dose descriptor:
- NOAEL
- Generation:
- F1
- Effect level:
- 400 mg/kg bw/day (nominal)
- Based on:
- test mat.
- Sex:
- male/female
- Basis for effect level:
- other: No change related to the test substance administration in the examination of viability index of pups, general clinical observation, body weight changes or necropsy findings in pups
- Reproductive effects observed:
- no
- Conclusions:
- There were no changes related to the test substance administration in the examination of reproduction performance, pregnancy, parturition, nursery condition, viability index of pups, general clinical observation, body weight changes or necropsy findings in pups.
On the basis of the above-mentioned results, the no-observed-adverse-effect level (NOAEL) and the no-observed-effect level (NOEL) of 2-(2-Vinyloxyethoxy) ethyl acrylate on the reproduction performance of the parental animals and on the development of pups were estimated to be 400 mg/kg/day under the conditions of this study because no changes related to the test substance administration were observed in the 400 mg/kg/day group. - Executive summary:
To investigate health effects of 2-(2-Vinyloxyethoxy) ethyl acrylate, combined repeated dose toxicity with reproduction/developmental toxicity study was performed in compliance with the OECD Guideline for Testing of Chemicals, No. 422. The test substance was repeatedly administered by oral gavage to male and female Crl:CD(SD) rats, 12 males and 12 females per group, at the doses of 0 (control, corn oil), 50, 140 and 400 mg/kg/day. The test substance was administered orally to male rats, before mating, during mating period and after mating, for a total of 91 days, and to female rats before mating, during mating and gestation periods, and up to day 5 after parturition, to investigate effects of its repeated administration on male and female rats, and effects on reproduction performance of males and females and development of pups. In the control and 400 mg/kg groups, 5 of the 12 males and 5 females were added to constitute recovery groups to investigate recovery in 14-day recovery period following administration. Females in the recovery group were not used for mating.
The results of this study are as follows:
1. Repeated dose toxicity In males and females in the low dose (50 mg/kg) and above groups, local irritation at the application site of the test substance was observed at the limiting ridge of the stomach and in the forestomach. These changes consisted of thickening in necropsy findings and squamous cell hyperplasia in histopathological findings, accompanied by ulcer and cellular infiltration of inflammatory cells.
In relation to the above changes, salivation was observed in the middle dose (140 mg/kg) and high dose (400 mg/kg) groups in the general clinical observation and detailed clinical observation; increases in white blood cell count, stab form and segmented neutrophils in the differential counts of white blood cells, and β-globulin fraction in males in the high dose group and decreases in albumin and A/G ratio, and increases in β-globulin fraction in females in the high dose group in hematology and biochemistry; decreases in absolute and relative thymus weights in males in the high dose group.
On the basis of the above-mentioned results, the no-observed-adverse-effect level (NOAEL) and the no-observed-effect level (NOEL) of 2-(2-Vinyloxyethoxy) ethyl acrylate were estimated to be less than 50 mg/kg/day in both of males and females under the conditions of this study because thickening in the forestomach and at the limiting ridge of the stomach, which was related to local irritation at the application site of the test substance, was observed at the doses of 50 mg/kg/day and above.
2. Reproductive and developmental toxicity
There were no changes related to the test substance administration in the examination of oestrous cycle, examination of reproduction performance, gestation, parturition and nursery condition, viability index of pups, general clinical observation, body weight changes or necropsy findings in pups. On the basis of the above-mentioned results, the no-observed-adverse-effect level (NOAEL) and the no-observed-effect level (NOEL) of 2-(2-Vinyloxyethoxy) ethyl acrylate on the reproduction performance of the parental animals and on the development of pups were estimated to be 400 mg/kg/day under the conditions of this study.
Reference
(Clinical signs)
Tables 1 and 2, show the general clinical observation results.
Males: There were no abnormal findings in the 0 (control group, expressed as the control group thereafter) or 50 mg/kg group (expressed as the low dose group thereafter).
In the 140 and 400 mg/kg groups (expressed as the middle and high dose groups, respectively thereafter), salivation was sporadically observed during the administration period, which was observed in higher frequency in a few males (animal no. 310 in the middle dose group and nos. 406, 408 and 411 in the high dose group).
One male (animal no. 310) in the middle dose group showed hematuria sporadically, and another (animal no. 306) showed soft feces only once.
Females: There were no abnormal findings in the control, low or middle dose group during the administration period.
In the high dose group, salivation was sporadically observed mainly in the administration period before mating, which was observed in higher frequency in 1 female (animal no. 458).
In the recovery groups, there were no abnormal findings in the control group, and salivation was sporadically observed in 1 female (animal no. 465) in the high dose group.
Tables 3 to 8 show the detailed clinical observation results.
Administration period
Males: Salivation was sporadically observed in the middle and high dose groups, and no significant changes were observed in any treatment group (low, middle or high dose group) as compared to the control group.
Females: Salivation was observed in the high dose group, and no significant changes were observed in any treatment group as compared to the control group.
Recovery period
Males: In the high dose group, there were no significant changes as compared to the control group.
Females: In the high dose group, there were no significant changes as compared to the control group.
Functional observational battery:
Tables 9 to 12 show the functional observational battery results, grip strength and locomotor activity measurements results.
Week 13 of administration
Males: There were no significant changes in functional observational battery results or grip strength in any treatment group as compared to the control group.
A transient and significant increase was observed in the locomotor activity measurements in the low dose group, which was not dose-dependent.
Females: There were no significant changes in the high dose group as compared to the control group.
Day 4 of lactation:
Females: A significant decrease was observed in the locomotor activity measurements in the low dose group as compared to the control group, which was not dose-dependent. There were no significant changes in the middle or high dose group.
Week 2 of recovery:
Males: There were no significant changes in the high dose group as compared to the control group.
Females: Significant increases were observed in grip strength of the hindlimbs in the high dose group as compared to the control group, which was not observed during week 13 of administration.
BODY WEIGHT AND FOOD CONSUMPTION (PARENTAL ANIMALS)
Figures 1 to 3, Tables 13 to 17 show the body weight changes.
Administration period
Males: In the low dose group, there were no significant changes in body weight changes, body weight gain, or percent body weight gain as compared to the control group.
In the middle dose group, there were no significant changes in body weight changes or body weight gain. Percent body weight gain significantly increased, which was not dose-dependent.
In the high does group, there were no significant changes in body weight changes or body weight gain. Percent body weight gain significantly decreased.
Females: There were no significant changes in body weight changes, body weight gain or percent body weight gain during the administration period before mating, gestation or lactation period, in any treatment group as compared to the control mgroup. In the high dose group in the recovery group, there were no significant changes in body weight changes or body weight gain. Percent body weight gain significantly increased.
Recovery period
Males: In the high dose group, there were no significant differences in body weight changes as compared to the control group, and body weight gain and percent body weight gain significantly increased.
Females: In the high dose group, there were no significant changes in body weight changes, body weight gain or percent body weight gain as compared to the
Food consumption:
Figures 4 to 6, Tables 18 to 22 show the food consumption.
Administration period
Males: There were no significant changes in any treatment group as compared to the control group.
Females: During the administration period before mating, there were no significant changes in any treatment group as compared to the control group. During the gestation period, there were no significant changes in the low or middle dose group. In the high dose group, food consumption significantly decreased on days 1 and 3 of gestation. During the lactation period, there were no significant changes in any treatment group.
In the high dose group in the recovery group, there were no significant changes.
Recovery period
Males: There were no significant changes in the high dose group as compared to the control group.
Females: Food consumption significantly increased in the high dose group on day 7 of recovery as compared to the control group.
Urinary findings:
Tables 23 to 26 show the urinary findings.
Week 13 of administration
Males: There were no significant changes in any treatment group as compared to the control group.
Females: There were no significant changes in the high dose group as compared to the control group.
Week 2 of recovery
Males: There were no significant changes in the high dose group as compared to the control group.
Females: There were no significant changes in the high dose group as compared to the control group.
TEST SUBSTANCE INTAKE (PARENTAL ANIMALS)
Not examined.
REPRODUCTIVE FUNCTION: ESTROUS CYCLE (PARENTAL ANIMALS)
Reproductive and developmental toxicity:
Examination of oestrous cycle
Tables 48 and 49 show the results of the examination of oestrous cycle.
Main test group
In the incidence of females showing normal oestrous cycle and the length of oestrous cycle, there were no significant differences in any treatment group as compared to the control group. In the 3 females in the low dose group and 1 female in each of the middle and high dose groups, which were determined to be persistent anestrus and their length of oestrous cycle was not calculated, copulation was observed in week 2 or 3 (re-mating period) of mating period. These females, except one in the low dose group and 2 in the middle dose group, were confirmed to be pregnant.
Recovery group:
In the high dose group set for investigation of recovery, there were no significant differences in the incidence of females showing normal oestrous cycle and the length of oestrous cycle, as compared to the control group. There were no females determined to be persistent anestrus.
Examination of reproduction performance:
Table 48 and INDIVIDUAL DATA 18-1 to 18-4 show the results of the examination of reproduction performance. Copulation was not observed in the 2-week mating period in 2 males in the low dose group and 1 male in each of the middle and high dose groups, but there were no significant differences in the copulation index as compared to the control group. As for the females paired with these males in the mating period, copulation with proved males was observed in the succeeding re-mating period. There were no significant differences in the fertility index, gestation index, duration of gestation, or nursing index on day 4 of lactation in any treatment group.
Pregnancy, parturition, nursery condition and viability index of pups Table 50 and INDIVIDUAL DATA 19-1 to 19-4 show the results of pregnancy, parturition, nursery condition and viability index of pups. There were no significant differences in the number of corpora lutea, number of implantations, implantation index, delivery index, number of pups delivered, sex ratio of pups, number of live pups and live birth index on day 0 of lactation, number of live pups and viability index on day 4 of lactation in any treatment group as compared to the control group.
ORGAN WEIGHTS (PARENTAL ANIMALS)
Organ weights
Tables 38 to 41 show the absolute and relative organ weights.
The end of administration period
Males: In the low and middle dose groups, there were no significant changes as compared to the control group. In the high dose group, absolute and relative thymus weights significantly decreased.
Females: In the low dose group, there were no significant changes as compared to the control group. In the middle dose group, relative liver weights significantly increased, which was not dose-dependent. In the high dose group, there were no significant changes.
The end of recovery period Males: In the high dose group, there were no significant changes as compared to the control group.
Females: In the high dose group, absolute weights of the kidney, adrenal and ovary significantly increased and the relative liver weights significantly increased as compared to the control group. These changes were not observed at the end of administration.
GROSS NECROPSY:
Necropsy findings
Tables 35 to 37 show the necropsy findings.
The end of administration period
Males: In the control group, atrophy of the right testis and epididymis was observed in 1 male.
In the low dose group, thickening of the limiting ridge of the stomach was observed in all of the 12 males. In the middle dose group, thickening of the limiting ridge of the stomach was observed in all of the 12 males, and diffuse (3 males) and multifocal (6 males) papillary thickening of the forestomach mucosa was observed.
In the high dose group, thickening of the limiting ridge of the stomach, diffuse papillary thickening of the forestomach mucosa, and hypertrophy of the pancreaticosplenic lymph node were observed in all of the 7 males. Multifocal black patches (1 male) and fine black patches (2 males) in the glandular stomach mucosa were observed.
Females: In the control group, there were no abnormal findings in any of the 12 females on day 6 of lactation.
In the low dose group, out of the 11 females on day 6 of lactation, focal thickening (1 female), multifocal thickening (1 female) and multifocal papillary thickening (1 female) of the forestomach mucosa were observed. There were no abnormal findings in the one non-pregnant female.
In the middle dose group, out of the 10 females on day 6 of lactation, thickening of the limiting ridge of the stomach was observed in 8 females, multifocal (4 females) and focal (1 female) papillary thickening of the forestomach mucosa, and focal (2 females), diffuse (1 female) and multifocal (1 female) thickening of the forestomach mucosa were observed. Among the non-pregnant 2 females, focal thickening of the forestomach mucosa was observed in 1 female, and thickening of the limiting ridge of the stomach and focal papillary thickening of the forestomach mucosa were observed in 1 female.
In the high dose group, thickening of the limiting ridge of the stomach and hypertrophy of the pancreaticosplenic lymph node were observed in all of the 12 females on day 6 of lactation. Diffuse (10 females) and multifocal (2 females) papillary thickening of the forestomach mucosa was observed, and adhesion to the lateral left lobe of the liver was observed in 1 female.
The end of recovery period
Males: In the control group, atrophy of the right testis and epididymis was observed in 1 male.
In the high dose group, thickening of the limiting ridge of the stomach and focal thickening of the forestomach mucosa were observed in 2 males, diffuse thickening of the forestomach mucosa was observed in 1 male, and diffuse (1 male) or multifocal papillary (1 male) thickening of the forestomach mucosa was observed. Hypertrophy of the pancreaticosplenic lymph node was observed in 3 males.
Females: There were no abnormal findings in any of the 5 females in the control group. In the high dose group, thickening of the limiting ridge of the stomach was observed in 2 females, and diffuse (1 female) and focal (4 females) thickening of the forestomach mucosa, and hypertrophy of the pancreaticosplenic lymph node in 4 females.
HISTOPATHOLOGY (PARENTAL ANIMALS)
Tables 42, 44, 45 and 47, show the histopathological findings.
Tables 43 and 46 show the results of stages of spermatogenesis in the testis.
The end of administration period
Males:
[Forestomach]
Squamous cell hyperplasia was observed in 1 (slight; +) of the 12 males in the low dose group, 9 (slight to severe; + to +++) of the 12 males in the middle dose group, and all (moderate to severe; ++ to +++) of the 7 males in the high dose group, and were significant differences in the middle and high dose groups as compared to the control group. Ulcer was observed in 1 male (+) in the middle dose group and 6 males (+ to ++) in the high dose group, and there was a significant difference in the high dose group. Submucosal cellular infiltration of inflammatory cells was observed in 8 males (+) in the middle dose group and all males (+ to ++) in the high dose group, and there were significant differences in the middle and high dose groups. Submucosal fibrosis was observed in 1 male (+) in the middle dose group and all (+ to ++) in the high dose group, and there was a significant difference in the high dose group. Submucosal edema was observed in 3 males (+) in the middle dose group.
[Limiting ridge of the stomach] Squamous cell hyperplasia was observed in all males, and there were significant differences in the low (+), middle and high (+ to ++) dose groups as compared to the control group. Ulcer was observed in 1 male (++) in the high dose group.
[Glandular stomach]
Eosinophilia of secretory granule of the chief cell was observed in 1 male (+) in each of the middle and high dose groups, and erosion in 3 males (+) in the high dose group.
[Pancreaticosplenic lymph node, at which gross findings were made at necropsy in all males in the high dose group]
Medullary proliferation of plasmacytes and reactive hyperplasia of the follicles were observed in all of the 7 males (+ to ++) and sinus dilatation was observed in 6 males (+ to ++).
[Other organs and tissues]
There were no findings related to the test substance administration or those with increasing incidence.
[Spermatogenesis in the testis]
In the high dose group, significant increases were observed in the number and the number per sertoli cell of pachytene spermatocytes and round spermatids in the stages VII to VIII as compared to the control group. There were no significant changes in the other Stages, and all of these significant differences were considered incidental and were not related to the test substance administration.
Females:
[Forestomach]
Squamous cell hyperplasia was observed in 3 (slight to moderate; + to ++) of the 12 females in the low dose group, 10 (slight to moderate; + to ++) of the 12 females in the middle dose group, and all (moderate to severe; ++ to +++) of the 12 females in the high dose group, and there were significant differences in the middle and high dose groups as compared to the control group. Ulcer was observed in 3 females (+ to ++) in the low dose group, 3 females (+) in the middle dose group, and 9 females (+ to ++) in the high dose group, and there was a significant difference in the high dose group. Submucosal cellular infiltration of inflammatory cells was observed in 3 females (+ to ++) in the low dose group, 10 females (+ to ++) in the middle dose group and 11 females (+ to ++) in the high dose group, and there were significant differences in the middle and high dose groups. Submucosal fibrosis was observed in 3 females (+ to ++) in the low dose group, 7 females (+ to ++) in the middle dose group, and 11 females (+ to ++) in the high dose group, and there were significant differences in the middle and high dose groups. Submucosal edema was observed in 2 females (+) in the low dose group, 7 females (+) in the middle dose group, and 3 females (+) in the high dose group, and there was a significant difference only in the middle dose group.
[Limiting ridge of the stomach]
Squamous cell hyperplasia was observed in 1 female (+) in the low dose group, and all in the middle (+) and high (+ to ++) dose groups, and there were significant differences in the middle and high dose groups as compared to the control group. [Pancreaticosplenic lymph node, at which gross findings were made at necropsy in all females in the high dose group] Medullary proliferation of plasmacytes was observed in all of the 12 females (++), reactive hyperplasia of the follicles in 9 females (+ to ++), and sinus dilatation in 2 females (+).
[Other organs and tissues]
There were no findings related to the test substance administration or those with increasing incidence.
The end of recovery period
Males:
[Forestomach]
Squamous cell hyperplasia was observed in all of the 5 males (+ to ++) in the high dose group, and there was a significant difference as compared to the control group. Submucosal cellular infiltration of inflammatory cells was observed in 4 males (+) in the high dose group, and there was a significant difference. Submucosal fibrosis was observed in 4 males (+ to ++).
[Limiting ridge of the stomach]
Squamous cell hyperplasia was observed in 4 males (+) in the high dose group, and there was a significant difference as compared to the control group. [Pancreaticosplenic lymph node, at which gross findings were made at necropsy in 3 males in the high dose group] Reactive hyperplasia of the follicles was observed in 3 males (+) and fibrosis in 2 males (+).
[Other organs and tissues]
There were no findings related to the test substance administration or those with increasing incidence.
[Spermatogenesis in the testis]
In the high dose group, significant increases were observed in the number of round spermatids in the Stages I to IV; the number per sertoli cell of pachytene spermatocytes, and the number and the number per sertoli cell of round spermatids in the Stages VII to VIII; the number per sertoli cell of pachytene/diplotene spermatocytes in the stages XII to XIV, as compared to the control group. These significant differences, as those at the end of administration, were considered incidental because there were no significant changes in the Stages IX to XI.
Females:
[Forestomach]
Squamous cell hyperplasia was observed in all (+) of the 5 females in the high dose group, and there was a significant difference as compared to the control group. Submucosal cellular infiltration of inflammatory cells was observed in 2 females (+) in the high dose group. Submucosal fibrosis was observed in all females (+ to ++), and there was a significant difference in the high dose group.
[Limiting ridge of the stomach]
Squamous cell hyperplasia was observed in 4 females (+) in the high dose group, and there was a significant difference as compared to the control group. [Pancreaticosplenic lymph node, at which gross findings were made at necropsy in 4 females in the high dose group] Reactive hyperplasia of the follicles was observed in 4 females (+), fibrosis in 3 females (+) and sinus dilatation in 1 female (+).
[Other organs and tissues]
There were no findings related to the test substance administration or those with increasing incidence.
HAEMATOLOGY
Hematological findings
Tables 27 to 30 show the hematological findings.
The end of administration period
Males: There were no significant changes in the low dose group as compared to the control group.
In the middle dose group, platelet count significantly increased, which was not dose-dependent.
In the high dose group, white blood cell count significantly increased. In the differential counts of white blood cells, stab form and segmented neutrophils significantly increased and lymphocytes significantly decreased.
Females: There were no significant changes in the low dose group as compared to the control group.
In the middle dose group, red blood cell count and hemoglobin concentration significantly decreased, which were not dose-dependent. In the high does group, there were no significant changes.
The end of recovery period
Males: In the high dose group, red blood cell count significantly decreased as compared to the control group, which was not observed at the end of administration.
Females: There were no significant changes in the high dose group as compared to the control group.
BIOCHEMICAL FINDINGS:
Tables 31 to 34 show the biochemical findings.
The end of administration period
Males: In the low dose group, there were no significant changes as compared to the control group. In the middle dose group, total cholesterol significantly increased, which was not dose-dependent.
In the high dose group, γ-GTP and β-globulin fraction significantly increased. Females: In the low dose group, there were no significant changes as compared to the control group.
In the middle dose group, calcium significantly increased, which was not dose-dependent. In the high dose group, albumin and A/G ratio significantly decreased, and potassium and β-globulin fraction significantly increased.
The end of recovery period
Males: In the high dose group, there were no significant changes as compared to the control group.
Females: In the high dose group, γ-GTP significantly increased as compared to the control group, and total bilirubin significantly decreased. These were not observed at the end of administration.
CLINICAL SIGNS (OFFSPRING)
Pups found dead at the observation at the end of parturition were as follows; 2 males and 1 female in the control group, 2 females in the low dose group, 2 males and 2 females in the middle dose group, and 1 male and 1 female in the high dose group.
Pups found dead and missing up to day 4 of lactation were as follows: 1 female in the control group, 5 males and 2 females in the low dose group, 3 females in the middle dose group, and 2 females in the high dose group.
Milk-band negative live and dead pups were sporadically observed in all treatment groups and there were no other abnormalities.
BODY WEIGHT (OFFSPRING)
There were no significant differences in males or females in any treatment group as compared to the control group.
SEXUAL MATURATION (OFFSPRING)
Not applicable
ORGAN WEIGHTS (OFFSPRING)
Not applicable
GROSS PATHOLOGY (OFFSPRING)
HISTOPATHOLOGY (OFFSPRING)
Not exammined for offspring
OTHER FINDINGS (OFFSPRING)
NECROPSY:
In the dead pups, dilatation of the renal pelvis in the kidney was observed in 2 males in the low dose group, and there were no other noticeable abnormal findings in males or females in any treatment group.
In the surviving pups on day 4 of lactation, yellowish brown discoloration of the liver was observed in 1 female in the control group, dilatation of the renal pelvis of the kidney in 2 females in the low dose group, and black mass in the liver of 1 female in the high dose group. There were no other abnormal findings in males or females in any treatment group.
To investigate health effects of 2-(2-Vinyloxyethoxy) ethyl acrylate, combined repeated dose toxicity with reproduction/developmental toxicity study was performed in compliance with the OECD Guideline for Testing of Chemicals, No. 422. The test substance was repeatedly administered by oral gavage to male and female Crl:CD(SD) rats, 12 males and 12 females per group, at the doses of 0 (control, corn oil), 50, 140 and 400 mg/kg/day. The test substance was administered orally to male rats, before mating, during mating period and after mating, for a total of 91 days, and to female rats before mating, during mating and gestation periods, and up to day 5 after parturition, to investigate effects of its repeated administration on male and female rats, and effects on reproduction performance of males and females and development of pups. In the control and 400 mg/kg groups, 5 of the 12 males and 5 females were added to constitute recovery groups to investigate recovery in 14-day recovery period following administration. Females in the recovery groups were not used for mating.
In general clinical observation, salivation was sporadically observed in the middle dose (140 mg/kg) and high dose (400 mg/kg) groups. These were observed also in detailed clinical observation, and there were no statistically significant differences. It was considered that the salivation was related to local irritation at the application site of the test substance because this disappeared after withdrawal and was not observed in the recovery period, and was observed also in the 28-day repeated dose toxicity study1). In one male in the middle dose group, hematuria was observed sporadically, which was considered incidental because this was not dose-dependent, and no changes were observed in the kidney at necropsy. In the functional observational battery, no changes related to the test substance administration were observed. In body weight changes, there were no significant changes in males or females during the administration period. In the high dose group, percent body weight gain significantly decreased in males during the administration period, and body weight gain and percent body weight gain significantly increased during the recovery period. These changes were considered to be indicative of recovery following withdrawal. In females in the recovery groups, percent body weight gain significantly increased during the administration period. Considering that there were no changes in body weight changes in males or females, and the significant differences observed in males and females were in the opposite direction, these changes were determined not toxicologically important.
Food consumption decreased significantly in females in the high dose group on days 1 and 3 of gestation, and increased in females in the high dose group on day 7 of recovery. These changes were not considered toxicologically important because significant differences were observed transiently.
In urinary findings, there were no changes related to the test substance administration.
In hematological findings, significant increases were observed in white blood cell count, stab form and segmented neutrophils in the differential counts of white blood cells in males in the high dose group. These changes were considered accompanying inflammatory changes in the forestomach, etc. in the necropsy and histopathological examination.
In biochemical findings, significant increases were observed in γ-GTP and β-globulin fraction in males, significant decreases in albumin and A/G ratio, and significant increases in potassium and β-globulin fraction in females in the high dose group. The changes in the protein fractions were considered accompanying inflammatory changes in the forestomach, etc. The significant increases in γ-GTP and potassium were not considered toxicologically important because the former did not accompany any hepatobiliary changes, and as for the latter, there were no changes in the parameters related to the renal function (urea nitrogen, creatinine), and because there were no histopathological changes in the liver or kidneys.
In necropsy findings, thickening of the limiting ridge of the stomach and focal thickening of the forestomach mucosa were observed in males and females in the low, middle and high dose groups, which were considered related to the test substance administration. Changes including the thickening of the limiting ridge of the stomach were observed at the doses of 160 mg/kg and above in the 28-day repeated dose study1), and it was considered that these occurred at the low dose group in this study because of, longer administration period. These changes were histopathologically squamous cell hyperplasia accompanied by ulcer and cellular infiltration of inflammatory cells. The areas involved were limited to the stomach and surrounding tissues (pancreaticosplenic lymph node), and the changes related to the test substance administration were limited to the application site (local irritation), and no other toxicity was observed.
In organ weights, significant decreases were observed in the absolute and relative thymus weights in males in the high dose group. These changes were considered stress-related or wasting changes accompanying inflammatory changes in the forestomach, etc.
Histopathological findings included squamous cell hyperplasia, etc. at the limiting ridge of the stomach and forestomach, which were irritating changes caused by the test substance, and there were no other changes related to the test substance administration. In spermatogenesis in the testis, there were no changes related to the test substance administration.
On the basis of the above-mentioned results, the no-observed-adverse-effect level (NOAEL) and the no-observed-effect level (NOEL) of 2-(2-Vinyloxyethoxy) ethyl acrylate were estimated to be less than 50 mg/kg/day in both of males and females under the conditions of this study because thickening of the forestomach and at the limiting ridge of the stomach, which was related to local irritation at the application site of the test substance, was observed at the doses of 50 mg/kg/day and above.
Reproductive and developmental toxicity
There were no changes related to the test substance administration in the examination of oestrous cycle in any treatment group in the main test and recovery test. As for the 3 females in the low dose group and 1 female in each of the middle and high dose groups, which were determined to be persistent anestrus and their length of oestrous cycle was not calculated, dose-dependency and relation to the test substance administration were not observed.
There were no changes related to the test substance administration in the examination of reproduction performance, pregnancy, parturition, nursery condition, viability index of pups, general clinical observation, body weight changes or necropsy findings in pups.
On the basis of the above-mentioned results, the no-observed-adverse-effect level (NOAEL) and the no-observed-effect level (NOEL) of 2-(2-Vinyloxyethoxy) ethyl acrylate on the reproduction performance of the parental animals and on the development of pups were estimated to be 400 mg/kg/day under the conditions of this study because no changes related to the test substance administration were observed in the 400 mg/kg/day group.
Effect on fertility: via oral route
- Endpoint conclusion:
- no adverse effect observed
- Dose descriptor:
- NOAEL
- 400 mg/kg bw/day
- Study duration:
- subacute
- Species:
- rat
- Quality of whole database:
- OECD guideline study and GLP study.
Effect on fertility: via inhalation route
- Endpoint conclusion:
- no study available
Effect on fertility: via dermal route
- Endpoint conclusion:
- no study available
Additional information
OECD 422 study:
The test substance was repeatedly administered by oral gavage to male and female Crl:CD(SD) rats, 12 males and 12 females per group, at the doses of 0 (control, corn oil), 50, 140 and 400 mg/kg/day. The test substance was administered orally to male rats, before mating, during mating period and after mating, for a total of 91 days, and to female rats before mating, during mating and gestation periods, and up to day 5 after parturition, to investigate effects of its repeated administration on male and female rats, and effects on reproduction performance of males and females and development of pups. In the control and 400 mg/kg groups, 5 of the 12 males and 5 females were added to constitute recovery groups to investigate recovery in 14-day recovery period following administration. Females in the recovery group were not used for mating. The results of this study are as follows:
Reproductive and developmental toxicity:
There were no changes related to the test substance administration in the examination of oestrous cycle in any treatment group in the main test and recovery test. As for the 3 females in the low dose group and 1 female in each of the middle and high dose groups,
which were determined to be persistent anestrus and their length of oestrous cycle was not calculated, dose-dependency and relation to the test substance administration were not observed.
There were no changes related to the test substance administration in the examination of oestrous cycle, examination of reproduction performance, gestation, parturition and nursery condition, viability index of pups, general clinical observation, body weight changes or necropsy findings in pups.
Effects on developmental toxicity
Description of key information
Key study: Pre-natal development toxicity (OECD 414)
The no-observed adverse effect level of VEEA was considered to be 400 mg/kg/day for fetuses under the present study conditions. VEEA was considered to have no adverse effects on the fetal organogenesis and development at doses up to 400 mg/kg/day.
Link to relevant study records
- Endpoint:
- developmental toxicity
- Remarks:
- pre-natal development toxicity
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Study period:
- In life phase: February 4 to July 16, 2019
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- guideline study
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 414 (Prenatal Developmental Toxicity Study)
- Deviations:
- yes
- Remarks:
- In the measurement of T3 on March 19, standard solutions were not appropriately measured. Remeasurement was performed on these samples, therefore, this event was not considered to affect the quality or integrity of the study results.
- GLP compliance:
- yes (incl. QA statement)
- Limit test:
- no
- Specific details on test material used for the study:
- Name: 2-(2-Vinyloxyethoxy) ethyl acrylate
Synonym: VEEA
Description: Colourless liquid
Lot No: 8K15
Purity: 99.6%
Supplier: Study sponsor
Storage conditions: Refrigerated - Species:
- rat
- Strain:
- other: Crl:CD(SD)
- Details on test animals or test system and environmental conditions:
- TEST ANIMALS
- Source: Charles River Laboratories Japan, Inc.
- Age at study initiation: 9 weeks
- Weight at study initiation: females weighed 186 to 234 g,
- Housing: Metal bracket cages (260 W x 380 D x 180 H, mm), with wire mesh floors. For females with successful copulation, small trays with bedding for experimental animals.
- Number of animals per cage: Two females during quarantine and mating period, 1 male during mating period, 1 female after group assignment; and 2 (1 male and 1 female) during mating
- Diet (e.g. ad libitum): Pellet diet, CRF-1, supplied freely from metal feeders.
- Water (e.g. ad libitum): Sapporo-City tap water, Supplied freely from the automatic watering system.
- Acclimation period: The period from animal receipt to the completion of obtaining pregnant females and group assignment was designated as the quarantine and mating period on a computer
system. Quarantine period: from the day of receipt ( quarantine and mating day 1, to quarantine and mating day 6 Acclimatization period: the period up to initiation of mating, including the quarantine period.
DETAILS OF FOOD AND WATER QUALITY:
Food quality: The diet of the lots used in this study was analyzed for contaminants that may affect the study. The analysis results of all items were within the acceptable ranges.
Drinking water: Samples of drinking water were collected at the end of the piping system of the animal room used in this study on January 7, and July 1, 2019, and analyzed for contaminants that may affect the study. The analysis results of all items were within the acceptable ranges.
ENVIRONMENTAL CONDITIONS
- Temperature (°C): 22°C +/- 3°C (actual range 21°C to 24°C)
- Humidity (%): 50% +/- 20% (actual range 38% to 57%)
- Air changes (per hr): 10 to 15
- Photoperiod (hrs dark / hrs light) 12 hours artificial lighting (from 8:00 to 20:00):
IN-LIFE DATES: From: 30th January, 2019 To: 16th July, 2019
Study Initiation: January, 28, 2019
Start of mating: 4th February, 2019
Start of administration: 11th February, 2019
Start of intrauterine observation at term: 25th February, 2019
End of fetal examination: 16th July, 2019
Study completion: 20th September, 2019 - Route of administration:
- oral: gavage
- Vehicle:
- corn oil
- Details on exposure:
- PREPARATION OF DOSING SOLUTIONS:
Preparation method: A required amount of the test article was accurately weighed out for each dose level, to which the vehicle was added to obtain each prescribed concentration, and the mixture was stirred with a stirrer to dissolve the test article.
Preparation frequency: Prepared 4 times at intervals of 7 days, and used within 7 days after preparation.
Storage conditions: Dosing solutions were placed in light-resistant containers, and stored at room temperature (actual range 21.0°C to 22.1°C).
ADMINISTRATION:
Method: Dosing solution was administered into the stomach by oral gavage using a disposble gastric tube and a disposable syringe.
Individual dose volume was calculated based on the body weight on the measurement day closest to the day of administration.
VEHICLE
- Name: Corn Oil
- Justification for use and choice of vehicle (if other than water): Test article stable in vehicle. - Analytical verification of doses or concentrations:
- yes
- Details on analytical verification of doses or concentrations:
- Confirmation of stability of dosing solutions:
Before the start of administration, the 2.5 and 100 mg/mL preparations were confirmed to be stable for 8 days ( counted from the day of preparation designated as day 0) at room temperature.
Confirmation of concentrations of dosing solutions: The concentrations of the test article in the dosing solutions of all concentrations were analyzed by HPLC at the first and final preparation. The analysis results confirmed that the concentrations of the dosing solutions were appropriate.
Instruments:
High performance liquid chromatography (HPLC) Waters system
Alliance Separations Module: e2695; Waters Corporation
UV-VIS Detector: 2489; Waters Corporation
HPLC Data processor: Empower 3; Waters Corporation
Reference standard
Name: 2-(2-Vinyloxyethoxy) ethyl acrylate
Synonym: VEEA
Lot No.: 8K15
Storage conditions: Refrigeration (actual range 3.0°C to 4.0°C), lightresistant, and airtight
HPLC conditions:
Column: Unison UK-C18, 3 μm, 4.6 mm I.D. x 250 mm, Imtakt Corporation
Mobile phase: Acetonitrile/0.1 % phosphoric acid solution (1:1)
Autosampler rinse solution: Acetonitrile/ultrapure water (1:1)
Flow rate: 0.8 mL/min
Wavelength: 211 nm
Column temperature: 40°c
Injection volume: 10 µL
Autosampler temperature: 10°c
Run time: 11 minutes
Criteria:
Stability test:
(1)At preparation: The content should be 100% ± 10.0%, RSD should not exceed 5.0%.
After storage: The remaining rate should be 100% ± 10.0%, RSD should not exceed 5.0%.
(2)Confirmation test of concentration:
The content should be 100% ± 10.0%, and the RSD should not exceed 5.0%.
(3)System suitability test:
The RSDs of the peak area and retention time should not exceed 2.0%.
Results:
(1) Stability test: The results met the criteria both at preparation and after storage
(2) Confirmation test of concentration: The results met the criteria.
(3) System suitability test: The results met the criteria (RSDs: 0.0% to 0.5%). - Details on mating procedure:
- MATING AND ASSIGNMENT OF MATED FEMALES TO TEST GROUPS:
Animals used: Animals that showed no abnormality in body weight gain or clinical signs during the quarantine and mating period were selected for this study.
Age of animals at initiation of mating: After the end of quarantine ( quarantine and mating day 6), mating was started at 29 weeks of age in males and at 9 weeks of age in females.
Mating procedure: Vaginal smears were taken from females for microscopic examination. Females showing proestrous vaginal smears were transferred to males' cages in the early evening and paired overnight with males on a 1: 1 basis. On the following morning, vaginal plugs and sperm in vaginal smears of the females were examined. Successful copulation was confirmed by the presence of sperm in vaginal smears. The day on which copulation is confirmed was designated as gestation day (GD) 0.
Mating period: The mating procedure was repeated during 11 days until the required number of mated females (24 females/group) was attained. Males were observed for clinical condition until the required number of mated females was obtained, and females were also observed until copulation.
Group assignment: On the day on which evidence of copulation was detected, females were weighed and distributed to test groups so that group means and standard deviations of body weight were as equal as possible, using the computer system (MiTOX). - Duration of treatment / exposure:
- The animals were dosed once daily from Gestation Day (GD) 6 to GD 19.
- Frequency of treatment:
- Once daily
- Duration of test:
- Start of mating: 4th Feb, 2019
End of fetal examination: 16th July, 2019 - Dose / conc.:
- 0 mg/kg bw/day
- Remarks:
- Control
- Dose / conc.:
- 10 mg/kg bw/day
- Remarks:
- Low dose
- Dose / conc.:
- 60 mg/kg bw/day
- Remarks:
- Middle dose
- Dose / conc.:
- 400 mg/kg bw/day
- Remarks:
- High dose
- No. of animals per sex per dose:
- Test Group: Dose mg(kg) Concentration (mg/mL) Dose volume (ml/kg) Number of mated females
Control 0 0 4.0 24
Low Dose: 10 2.5 4.0 24
Middle dose: 60 15 4.0 24
High dose 400 100 4.0 24 - Control animals:
- yes, concurrent vehicle
- Details on study design:
- Details on study design:
A prenatal developmental toxicity study was performed to investigate potential effects of VEEA on dams and embryo-fetal organogenesis and development. VEEA was orally administered to Crl:CD(SD) rats, 24 mated females per group, at 0, ( control), 10, 60, and 400 mg/kg/day from gestation days 6 to 19. Fetuses were removed from the uterus at the necropsy of dams on gestation day 20, and external, visceral and skeletal examinations were performed.
Rational for dose selection:
In the combined repeated dose toxicity study with the reproduction and developmental toxicity study of the test article, the test article was administered by oral gavage at 0, 50, 140, and 400 mg/kg to 12 female rats per group from 14 days before the start of mating to 5 days after parturition. In that study, thickening of the limiting ridge of the stomach or the forestomach mucosa was noted at 50 mg/kg and higher doses and salivation was noted at 400 mg/kg in dams; however, no effects of the test article administration were noted on the reproductive performance of parental animals or on the offspring.
Based on these results, the high dose was set at 400 mg/kg, which is expected to cause clear changes in dams, and the middle and low doses were set at 60 and 10 mg/kg, respectively, with a common ratio of approximately 6. - Maternal examinations:
- CAGE SIDE OBSERVATIONS: Yes
- Time schedule: From GD 0 to the day of necropsy.
Animals were examined for mortality, external appearance, behavior, and other changes. Animals were checked twice daily during the administration period (before and after dosing), and once daily during the other periods.
- Frequency: Twice daily during the administration period (before and after dosing), and once daily during the other periods
DETAILED CLINICAL OBSERVATIONS: Yes
- Time schedule: From GD 0 to the day of necropsy.
- Frequency: Twice daily during the administration period (before and after dosing), and once daily during the other periods
BODY WEIGHT: Yes
- Time schedule for examinations: Body weight measurements were performed on GD's 0, 3, 6, 9, 12, 15, 18 and 20.
- Body weight game calculation: Body weight on GD 6 was subtracted from each value measured on and after GD 9 to calculate the body weight gain.
- Adjusted body weight: Adjusted body weight = body weight on GD 20 - gravid uterine weight.
FOOD CONSUMPTION AND COMPOUND INTAKE (if feeding study): Yes
- Measurement days: On GDs 0, 3, 6, 9, 12, 15, 18, 20
- Food consumption for each animal determined and mean daily diet consumption calculated as g food/kg body weight/day: Yes
WATER CONSUMPTION AND COMPOUND INTAKE (if drinking water study): No
NECROPSY:
Time schedule: Animals were necropsied on GD 20
Method: After observation of external appearance and blood collection under anesthesia with isoflurane, animals were euthanized by exsanguination and grossly examined for organs and tissues. The thyroid and gross lesions were fixed and preserved in I 0% neutral buffered formalin.
POST-MORTEM EXAMINATIONS: Yes
Measurements performed: Thyroid weight measurements and histopathology of the thyroid.
OTHER:
Measurement of serum hormone concentration was examined in all animals at necropsy - Ovaries and uterine content:
- The ovaries and uterine content was examined after termination: Yes (at necropsy on GD 20)
Examinations included:
Gravid uterine weight, the numbers of corpora lutea, implantations, live fetuses, dead or resorbed embryos and fetuses, weight of live fetuses, and sex of live fetuses.
At necropsy of maternal rats, the ovaries and uteri were removed, and gravid uterine weight was measured with an electronic balance. Then, the uterine wall was dissected to observe the intrauterine condition and life and death of embryos and fetuses, and condition of their placentas, and the number of implantations was recorded. Live fetuses were removed from the uterus and individually weighed with an electronic balance. Live fetuses were sexed by external observation of the length between the anus and genitalia. When comparing the sex determination results and those based on the internal reproductive organs, there was no inconsistency in any fetuses. The number of corpora lutea in the ovaries was recorded. The ovaries and uterus after examination were preserved in 10% neutral buffered formalin by litter. The placentas after examination for anomalies were discarded. The uterus of the animal No. 50262, in which no uterine implants were grossly apparent, was stained with 10% ammonium sulfide solution and implantation sites were detected. - Fetal examinations:
- Anogenital distance:
Animals measured: All live fetuses
Method: The length between the anus and genitalia (AGD) of each fetus was measured and recorded. Litter mean AGD for each sex was calculated. In addition, litter mean AGD was divided by the cube root of its litter mean body weight by sex.
Fetal external examination:
Animals examined: All live fetuses
Method: At term of pregnancy, live fetuses were examined for external anomalies. After the examination, fetuses were euthanized by an intraperitoneal injection of pentobarbital sodium. Then, approximately one-half of the live fetuses in each litter was fixed in Bouin's solution for visceral examination. The remaining half of the fetuses were eviscerated, and then fixed in 99.5% ethanol for skeletal examination. When eviscerating the fetuses for skeletal examination, sex of the internal reproductive organ and presence or absence of malposition of the testis of males were recorded. The observation revealed no malposition of the testis in any male fetuses.
Calculation: The following indices were calculated:
Incidence of feta! external anomalies (%) = (number of fetuses showing external anomalies/ number of fetuses examined) x 100
Incidence of dams having fetuses with external anomalies = number of dams having fetuses with external anomalies / number of litters examined
Fetal visceral examination:
Animals examined: Visceral examination was performed for all fetuses fixed in Bouin's solution.
Method: Fetuses fixed in Bouin's solution were transferred to 70% ethanol before examination and then examined for presence or absence of visceral variations and anomalies macroscopically or under a stereoscopic microscope. The head was examined according to Wilson's free-hand sectioning method3l, the thoracic region was examined according to Nishimura's microdissection method4l, and the abdominal region was examined by the microdissection method. After the completion of these examinations, the fetuses were individually stored in 70% ethanol.
Calculation:
Incidence of fetal visceral variations (%) = (number of fetuses with visceral variations/ number of fetuses examined) x 100
Incidenece of litters with fetal visceral variations = number of dams having fetuses with visceral variations / number of litters examined.
Fetal skeletal examination:
Animals examined: Skeletal examination was performed for all skeletal specimens prepared.
Method: All fetuses fixed in 99.5% ethanol in all test groups were stained with alizarin red S, and then penetrated by KOH aqueous solution, followed by successive immersion in 50% and 70% glycerin aqueous solutions to prepare clear skeletal specimens. The numbers of ossified bones were counted under a stereoscopic microscope and the fetuses were examined for presence or absense of skeletal variations and anomalies.
Calculation:
Incidence of fetal skeletal variations (%) = (number of fetuses with skeletal variations / number of fetuses examined ) x 100
Incidence of fetal skeletal anomalies (%) = (number of fetuses with skeletal anomalies / number of fetuses examined) x 100
Incidence of litters with fetal skeletal variations = number of dams having fetuses with skeletal variations / number of litters examined
Incidence of litters with fetal skeletal anomalies = number of dams having fetuses with skeletal anomolies / number of litters examined - Statistics:
- Statistical analyses were performed using the computer system (MiTOX). The data in the test article groups and those in the control group were compared using the procedures shown below. In the feta! data, litter averages were used as the unit for statistical evaluation.
Means and standard deviations were calculated for the results of the following data:
body weight, adjusted body weight, body weight gain, food consumption, gravid uterine weight, and thyroid weight of maternal rats, numbers of corpora lutea, implantations, live fetuses, and dead or resorbed embryos and fetuses, and weight of live fetuses (by sex), and degree of ossification, which were analyzed for homogeneity of variances by the Bartlett test.
Means and standard deviations were calculated for the results of the following data:
preimplantation loss, implantation index, postimplantation loss, postimplantation loss in early stage and that in late stage, incidences of feta! anomalies or variations, and incidence of anomalous placentas, which were analyzed by Steel's test to detect any statistically significant difference between the test article and control groups. Fisher's exact probability test was used for data on the feta! sex ratio and incidences of litters having fetuses with anomalies or variations and dams with anomalous placentas.
Statistically significance level was set at 5% for comparison analysis with the control group. - Indices:
- Classification of dead or resorbed embryos and fetuses:
Embryo-fetal resorptions and deaths were classified into implantation sites and placental remnants (in the early stage of gestation after implantation) and macerated fetuses and dead term fetuses (in the late stage of gestation) according to the developmental stage at which they occurred.
Identification of live fetuses:
Calculation:
Individual identification of all live fetuses was performed in each litter. Preimplantation loss, implantation index, postimplantation loss, postimplantation loss in the early stage, postimplantation loss in the late stage, and incidence of anomalous placentas were calculated for each litter, and sex ratio and incidence of litters with anomalous placentas were calculated for each group by the following equations:
Preimplantation loss (%) = [ (number of corpora lutea ~ number of implantations) / number of corpora lutea] x 100
Implantation index (%) = (number of implantations/ number of corpora lutea) x 100
Postimplantation loss (%) = (number of dead or resorbed embryos and fetuses / number of implantations) x 100
Postimplantation loss in the early stage (%) = (number of early embryo-feta! deaths/ number of implantations) x 100
Postimplantation loss in the late stage (%) = (number oflate embryo-feta! deaths/ number of implantations) x 100
Sex ratio (%) = (total number oflive male fetuses / total number oflive fetuses) x 100
Incidence of anomalous placentas (%) = (number of anomalous placentas/ number of placentas examined) x I 00
Incidence of litters with anomalous placentas = number of dams with anomalous placentas/ number of litters examin - Clinical signs:
- no effects observed
- Description (incidence and severity):
- No abnormal findings were noted in clinical observation in any animal before the start of administration.
During the administration period and on the necropsy day, no abnormal findings were noted in clinical observation in any animal before and after dosing. No deaths occurred in any test group. - Dermal irritation (if dermal study):
- not examined
- Mortality:
- no mortality observed
- Description (incidence):
- No deaths occurred in any test group.
- Body weight and weight changes:
- effects observed, treatment-related
- Description (incidence and severity):
- In the 400 mg/kg group, body weight was significantly lower that that in the control group from GD 15 to GD 20. In this group, adjusted body weight was also significantly low. In the 60 ro 10 mg/kg group, no significant differences were noted.
In the 400 mg/kg group, body weight gain was significantly lower than that in the control group throughout the administration period. In the 60 or 10 mg/kg group, no significant differences were noted. - Food consumption and compound intake (if feeding study):
- effects observed, treatment-related
- Description (incidence and severity):
- In the 400 mg/kg group, food consumption was lower than that in the control group throughout the administration period, with statistically significant differences from GD 9 to GD 18. In the 60 or 10 mg/kg group, no significant differences were noted.
- 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:
- no effects observed
- Description (incidence and severity):
- No significant differences were noted in the absolute or relative thyroid weight of maternal rats in any test article group compared with that in the control group.
No significant differences were noted in the gravid uterine weight in any test article group compared with that in the control group. - Gross pathological findings:
- effects observed, treatment-related
- Description (incidence and severity):
- In the 400 mg/kg group, focal thickening of mucosa in the forestomach was noted in 15 maternal rats. In the 60 or 10 mg/kg group, no abnormalities were noted.
- Neuropathological findings:
- not examined
- Histopathological findings: non-neoplastic:
- effects observed, non-treatment-related
- Description (incidence and severity):
- Histopathological findings of the thyroid:
Remnant of ultimobranchial body was occasionally noted in each gronp, which was considered unrelated to the test article administration because this is a congenital change. No other abnormalities were noted in any animal. - Histopathological findings: neoplastic:
- not examined
- Other effects:
- effects observed, non-treatment-related
- Description (incidence and severity):
- Serum hormone concentration (T3, T4 and TSH):
In the 400 mg/kg group, serum T4 concentration was significantly higher than that in the control group; however no changes were noted in serum T3 or TSH concentration. In the 60 or 10 mg/kg group, no significant differences were noted in any serum hormone concentration. - Number of abortions:
- no effects observed
- Description (incidence and severity):
- No significant differences were noted in the numbers of numbers of dead fetuses and live fetuses in any test article group compared with that in the control group.
All females with successful copulation were confirmed pregnant, and live fetuses were obtained from all of them except one (animal No. 50262) that had implantation sites only. - Pre- and post-implantation loss:
- no effects observed
- Description (incidence and severity):
- No significant differences were noted in the numbers of corpora lutea and implantations, preimplantation loss, implantation index, postimplantation loss in any test article group compared with that in the control group.
- Total litter losses by resorption:
- no effects observed
- Early or late resorptions:
- no effects observed
- Dead fetuses:
- no effects observed
- Description (incidence and severity):
- No significant differences were noted in the numbers of numbers of dead fetuses and live fetuses in any test article group compared with that in the control group.
- Changes in pregnancy duration:
- no effects observed
- Changes in number of pregnant:
- no effects observed
- Description (incidence and severity):
- All females with successful copulation were confinned pregnant, and live fetuses were obtained from all of them except one (animal No. 50262) that had implantation sites only.
- Other effects:
- no effects observed
- Description (incidence and severity):
- The examination of placentas showed no abnormalities in any test groups including the control group.
- Key result
- Dose descriptor:
- NOAEL
- Effect level:
- 60 mg/kg bw/day (nominal)
- Based on:
- test mat.
- Basis for effect level:
- body weight and weight gain
- food consumption and compound intake
- other: Oral administration of test article to dams was considered to induce inhibition of body weight gain and food intake and thickening of the forestomach mucosa in dams at 400 mg/kg/day. The NOAEL was considered 60 mg/kg/day for dams.
- Abnormalities:
- no effects observed
- Fetal body weight changes:
- no effects observed
- Description (incidence and severity):
- No significant differences were noted for fetal weight for either sex in any test article group compared with that in the control group.
- Reduction in number of live offspring:
- no effects observed
- Description (incidence and severity):
- No significant differences were noted in the numbers of dead fetuses and live fetuses any test article group compared with that in the control group.
- Changes in sex ratio:
- no effects observed
- Description (incidence and severity):
- No significant differences were noted in the fetal sex ratio in any test article group compared with that in the control group.
- 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):
- External anomalies noted were thread-like tail in one fetus (group mean incidence per litter: 0.26%) in the control group, and two runts (0.57%) in the 10 mg/kg group.
In the fetal or litter incidence of these anomalies, no significant differences were noted in any test article group compared with the control group. No anomalies were noted in the 60 or 400 mg/kg group. - Skeletal malformations:
- effects observed, non-treatment-related
- Description (incidence and severity):
- A number of skeletal variations were noted in test and control groups.
In the fetal or litter incidences of these skeletal variations, no significant differences were noted in any test article group compared with the control group. There was no skeletal anomaly in any fetus in any test group.
No significant differences were noted in the mean numbers of ossifications of sacrocaudal centrum or stemebra in any test article group compared with the control group. - Visceral malformations:
- effects observed, non-treatment-related
- Description (incidence and severity):
- Visceral variations were noted as follows: thymic remnant in the neck in 5 (group mean incidence per litter: 2.70%), 7 (3.78%), 4 (2.48%), and 2 (1.29%) fetuses in the control, 10, 60, and 400 mg/kg groups, respectively. Left umbilical artery in 1 (0.60%) and 1 (0.52%) fetuses in the control and 60 mg/kg groups, respectively. In the fetal or litter incidences of these variations, no significant differences were noted in any test article group compared with the control group.
There was no visceral anomaly in any fetus in any test group. - Other effects:
- no effects observed
- Description (incidence and severity):
- Anogenital distances of fetuses:
No significant differences were noted in AGD or AGD per cube root of body weight ratio in males or females in any test article group compared with that in the control group. - Key result
- Dose descriptor:
- NOAEL
- Effect level:
- 400 mg/kg bw/day (nominal)
- Based on:
- test mat.
- Sex:
- male/female
- Basis for effect level:
- other: The test article was considered to have no adverse effects on organogenesis and development of fetuses at doses up to 400 mg/kg/day
- Key result
- Abnormalities:
- no effects observed
- Key result
- Developmental effects observed:
- no
- Conclusions:
- Oral administration of VEEA to dams was considered to induce inhibition of body weight gain and food intake and thickening of the forestomach mucosa in dams at 400 mg/kg/day, and was not considered to have any effect on the fetuses at doses up to 400 mg/kg/day.
On the basis of these results, the no-observed adverse effect level of VEEA was considered 60 mg/kg/day for dams, and 400 mg/kg/day for fetuses under the present study conditions. In addition, VEEA was considered to have no adverse effects on the fetal organogenesis and development at doses up to 400 mg/kg/day. - Executive summary:
A prenatal developmental toxicity study was performed to investigate potential effects of VEEA on dams and embryo-fetal organogenesis and development. VEEA was orally administered to Crl:CD(SD) rats, 24 mated females per group, at 0 ( control), 10, 60, and 400 mg/kg/day from gestation days 6 to 19. Fetuses were removed from the uterus at the necropsy of dams on gestation day 20, and external, visceral and skeletal examinations were performed.
In dams, food consumption, body weight and body weight gain during the administration period and adjusted body weight on gestation day 20 were low and focal thickening of the forestomach mucosa was noted in necropsy in the 400 mg/kg group. In the 10 or 60 mg/kg group, no changes related to the test article administration were noted in the dams.
In thyroid function related hormones, weight and histopathology of the thyroid, and uterine weight and ovary and uterine content at necropsy on gestation day 20, no effects of the test article administration were noted at doses up to 400 mg/kg.
In AGD, external appearance, and visceral and skeletal examination of fetuses, no changes related to the test article administration were noted.
On the basis of these results, oral administration of VEEA to dams was considered to induce inhibition of body weight gain and food intake and thickening of the forestomach mucosa in dams at 400 mg/kg/day, and was not considered to have any effect on the fetuses at doses up to 400 mg/kg/day.
On the basis of these results, the no-observed adverse effect level of VEEA was considered 60 mg/kg/day for dams, and 400 mg/kg/day for fetuses under the present study conditions. In addition, VEEA was considered to have no adverse effects on the fetal organogenesis and development at doses up to 400 mg/kg/day.
Reference
A prenatal developmental toxicity study was performed to investigate potential effects of VEEA on dams and embryo-fetal organogenesis and development. VEEA was orally administered to Crl:CD(SD) rats, 24 mated females per group, at 0 ( control), 10, 60, and 400 mg/kg/day from GD 6 to GD 19.
In dams, food consumption, body weight and body weight gain during the administration period and adjusted body weight on GD 20 were low in the 400 mg/kg group, which were considered effects of the test article administration. In addition, necropsy revealed focal thickening of the forestomach mucosa, which was considered an effect of the test article administration because the same change was noted also in the combined repeated dose toxicity with reproduction/developmental toxicity study. In this group, serum T4 concentration was significantly high in dams. This was considered toxicologically insignificant because no changes were noted in the thyroid weight or serum TSH concentration, and histopathological examination of the thyroid revealed no abnormalities related to the test article administration. In the 10 or 60 mg/kg group, no changes related to the test article administration were noted in the dams.
In the uterine weight and examination of ovary and uterine content at necropsy on GD 20, no changes were noted in any test article group, and the embryo/fetal survival or fetal development was not considered affected at doses up to 400 mg/kg.
In fetal AGD, effects of the test article administration were not noted in males or females at doses up to 400 mg/kg. In external appearance of fetuses, 2 runts were observed in the 10 mg/kg group. This was not considered related to the test article administration because no runts were noted in the higher dose groups and there were no significant differences in its fetal or litter incidences compared with the control group.
Fetal visceral examination revealed no visceral anomalies in any test article group.
Visceral variations of thymic renmant in the neck or left umbilical artery were occasionally noted in each group. These were considered unrelated to the test article administration because there were no significant differences in their fetal or litter incidences compared with the control group.
In fetal skeletal examination, no anomalies were noted in any test article group. Skeletal variations including dumbbell ossification of sternebra, short 13th rib, short thoracolumbar supernumerary rib, and bipartite/dumbbell ossification of thoracic centrum were noted in each group. These were considered unrelated to the test article administration because there is no significant difference in their fetal or litter incidences compared with the control group. In degrees of ossification of fetuses, no effects of the test article administration were noted.
On the basis of these results, oral administration of VEEA to dams was considered to induce inhibition of body weight gain and food intake and thickening of the forestomach mucosa in dams at 400 mg/kg/day, and was not considered to have any effect on the fetuses at doses up to 400 mg/kg/day.
Therefore, the no-observed adverse effect level of VEEA was considered 60 mg/kg/day for dams, and 400 mg/kg/day for fetuses under the present study conditions. In addition, VEEA was considered to have no adverse effects on organogenesis and development of fetuses at doses up to 400 mg/kg/day.
Effect on developmental toxicity: via oral route
- Endpoint conclusion:
- no adverse effect observed
- Dose descriptor:
- NOAEL
- 400 mg/kg bw/day
- Study duration:
- subacute
- Species:
- rat
- Quality of whole database:
- OECD guideline study and GLP study.
Effect on developmental toxicity: via inhalation route
- Endpoint conclusion:
- no study available
Effect on developmental toxicity: via dermal route
- Endpoint conclusion:
- no study available
Additional information
A prenatal developmental toxicity study was performed to investigate potential effects of VEEA on dams and embryo-fetal organogenesis and development. VEEA was orally administered to Crl:CD(SD) rats, 24 mated females per group, at 0 ( control), 10, 60, and 400 mg/kg/day from gestation days 6 to 19. Fetuses were removed from the uterus at the necropsy of dams on gestation day 20, and external, visceral and skeletal examinations were performed.
In dams, food consumption, body weight and body weight gain during the administration period and adjusted body weight on gestation day 20 were low and focal thickening of the forestomach mucosa was noted in necropsy in the 400 mg/kg group. In the 10 or 60 mg/kg group, no changes related to the test article administration were noted in the dams.
In thyroid function related hormones, weight and histopathology of the thyroid, and uterine weight and ovary and uterine content at necropsy on gestation day 20, no effects of the test article administration were noted at doses up to 400 mg/kg.
In AGD, external appearance, and visceral and skeletal examination of fetuses, no changes related to the test article administration were noted.
On the basis of these results, oral administration of VEEA to dams was considered to induce inhibition of body weight gain and food intake and thickening of the forestomach mucosa in dams at 400 mg/kg/day, and was not considered to have any effect on the fetuses at doses up to 400 mg/kg/day.
On the basis of these results, the no-observed adverse effect level of VEEA was considered 60 mg/kg/day for dams, and 400 mg/kg/day for fetuses under the present study conditions. In addition, VEEA was considered to have no adverse effects on the fetal organogenesis and development at doses up to 400 mg/kg/day.
Justification for classification or non-classification
Based on the results of an OECD 422 Combined Repeated Dose Toxicity with Reproduction/ Developmental Toxicity Study in Rats,
there is no evidence that the substance has an adverse effect on reproduction or development at the highest dose level tested (400 mg/kg bw/day). The substance is therefore not classified for reproductive toxicity based on this study.
Based on the results of a pre-natal developmental toxicity study (OECD 414) there were no reported effects for offspring development. VEEA was considered to have no adverse effects on the fetal organogenesis and development at doses up to 400 mg/kg/day. The substance is therefore not classified for reproductive toxicity.
Additional information
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Reproduction or further distribution of this information may be subject to copyright protection. Use of the information without obtaining the permission from the owner(s) of the respective information might violate the rights of the owner.
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