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EC number: 239-269-6 | CAS number: 15217-42-2
- 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
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- 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
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- Additional physico-chemical information
- Additional physico-chemical properties of nanomaterials
- Nanomaterial agglomeration / aggregation
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- Endpoint summary
- Stability
- Biodegradation
- Bioaccumulation
- Transport and distribution
- Environmental data
- Additional information on environmental fate and behaviour
- Ecotoxicological Summary
- Aquatic toxicity
- Endpoint summary
- Short-term toxicity to fish
- Long-term toxicity to fish
- Short-term toxicity to aquatic invertebrates
- Long-term toxicity to aquatic invertebrates
- Toxicity to aquatic algae and cyanobacteria
- Toxicity to aquatic plants other than algae
- Toxicity to microorganisms
- Endocrine disrupter testing in aquatic vertebrates – in vivo
- Toxicity to other aquatic organisms
- Sediment toxicity
- Terrestrial toxicity
- Biological effects monitoring
- Biotransformation and kinetics
- Additional ecotoxological information
- Toxicological Summary
- Toxicokinetics, metabolism and distribution
- Acute Toxicity
- Irritation / corrosion
- Sensitisation
- Repeated dose toxicity
- Genetic toxicity
- Carcinogenicity
- Toxicity to reproduction
- Specific investigations
- Exposure related observations in humans
- Toxic effects on livestock and pets
- Additional toxicological data

Developmental toxicity / teratogenicity
Administrative data
- Endpoint:
- developmental toxicity
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Study period:
- September 2019 - April 2020
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- guideline study
Data source
Reference
- Reference Type:
- study report
- Title:
- Unnamed
- Year:
- 2 020
- Report date:
- 2020
Materials and methods
Test guideline
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 414 (Prenatal Developmental Toxicity Study)
- GLP compliance:
- yes (incl. QA statement)
- Limit test:
- no
Test material
- Reference substance name:
- 1,2,3 Benzotriazole
- IUPAC Name:
- 1,2,3 Benzotriazole
Constituent 1
- Specific details on test material used for the study:
- SOURCE OF TEST MATERIAL
- Source and lot/batch number of test material: Connect Chemicals GmbH, 19303
- Expiration date of the lot/batch: 02.2021
- Production date: 03.2019
STABILITY AND STORAGE CONDITIONS OF TEST MATERIAL
-Stability of the test item in the vehicle prepared at concentrations of 12 and 110 mg/mL was
confirmed following storage for 7 days at room temperature (the temperature range, 20 – 25
°C) during method validation study. In addition, homogeneity analysis was performed for
formulations of 12 and 110 mg/mL after 4 days of storage after re-mixing
Test animals
- Species:
- rat
- Strain:
- Sprague-Dawley
- Details on test animals or test system and environmental conditions:
- TEST ANIMALS
- Source: The Lab Animals Breeding Center “Pushchino”, Branch of
Institute of Bioorganic Chemistry RAS:
Nauki 6, Puschino, Moscow region, Russia 142290
- Age at study initiation: Approximately 11-12 weeks old at the initiation of dose
administration on G5 (day 1)
- Weight at study initiation: 233 ± 15 g, N = 93
- Fasting period before study: no
- Housing: After identification and until mating, all females were housed by groups. Males were housed
alone, and females cohabited with a male in the home cage of the male (2:1). After confirmed
mating, dams were housed alone until euthanasia on gestation day 20
- Diet (e.g. ad libitum): ad libitum
- Water (e.g. ad libitum): ad libitum
- Acclimation period: ca 7-8 weeks, The animals were received at the age of 4 weeks
by separate litters to avoid of sibling mating
ENVIRONMENTAL CONDITIONS
- Temperature (°C): 20 - 24 °C
- Humidity (%): 30-70%
- Air changes (per hr): 12
- Photoperiod (hrs dark / hrs light): 12/ 12
IN-LIFE DATES: From: To:
Administration / exposure
- Route of administration:
- oral: gavage
- Vehicle:
- polyethylene glycol
- Details on exposure:
- PREPARATION OF DOSING SOLUTIONS:
The Sponsor provided the test item as a neat solid substance. Calculations for the preparation of formulations were based on the dose (36, 120 and 330 mg/kg bw) and administered volume (3 mL/kg body weight), were documented in Excel spreadsheets, and maintained in the study file as printouts.
The test item was dissolved in the required volume of the vehicle (Kollisolv® PEG E 400) in
order to achieve the concentrations of 12, 40, and 110 mg/mL and then homogenized using a magnetic stirrer.
Test item formulations were prepared every four days, aliquoted to the required volumes of days of the administration, and stored in tightly closed glass jars at room temperature in the
dark. For the control group, the required volume per day of Kollisolv® PEG E 400 was placed in a labeled jar.
VEHICLE
- Justification for use and choice of vehicle (if other than water): based on preliminary studies, the vehicle was chosen
- Concentration in vehicle: 12, 40, and 110 mg/mL
- Amount of vehicle (if gavage): 3 mL/kg body weight
- Lot/batch no. (if required): BCCB1456
- Purity: not stated - Analytical verification of doses or concentrations:
- yes
- Details on analytical verification of doses or concentrations:
- Stability of the test item in the vehicle prepared at concentrations of 12 and 110 mg/mL was
confirmed following storage for 7 days at room temperature (the temperature range, 20 – 25
°C) during method validation study. In addition, homogeneity analysis was performed for
formulations of 12 and 110 mg/mL after 4 days of storage after re-mixing.
Analysis of formulations for homogeneity and concentration during dosing period was
conducted in the test facility at the beginning, in the middle and at the end of
in-life phase using a validated method.
For homogeneity analysis, quadruplicate samples (approximately 0.1 mL of each) were
collected from the top, middle and bottom strata of each dosing formulation prepared during
the study.
For concentration analysis, quadruplicate samples were collected from the middle stratum of
each dosing formulation (including the vehicle control group) prepared during the study.
Samples collected from the mean stratum for homogeneity analysis used for this purpose.
A pair of quadruplicate samples from each strata was used for analysis, the other pair was
stored as back-up samples at room temperature in tightly closed flasks, analyzed if necessary
based on primary assays to verify concentration and were discarded after the study director's
approval of the analytical results.
Acceptance criteria for the formulations analysis are based on the test item in vehicle
composition as a suspension. For stability, the mean concentration of formulation samples of
12 and 110 mg/mL after 4 days of storage and resuspension should be within the acceptable
range of the target concentration (85-115% with RSD<10%), and within the range 85-115% of
the time zero point. The actual concentration of analyzed samples collected from the mean
stratum of formulations should be within the range of 85% - 115% of the target concentration.
The acceptance criteria for homogeneity are RSD<10% with the mean concentration within
85% to 115% of the target concentration. - Details on mating procedure:
- After identification, females were monitored to an estrous cyclicity daily during 3-5 days. Females with
clear stages of estrous cycle in vaginal smear were cohabited with a male (avoiding siblings mating),
2:1 until mating. Positive evidence of mating was confirmed by the presence of a vaginal copulatory
plug or the presence of sperm following a vaginal lavage. Each mating female was examined daily on
the morning. The day when evidence of mating was identified is termed as gestation day 0 (G0). - Duration of treatment / exposure:
- 15 days, from day 5 to day 19 (including) of post mating (G5-G19)
- Frequency of treatment:
- daily
- Duration of test:
- Until Gestation day 20
Doses / concentrationsopen allclose all
- Dose / conc.:
- 36 mg/kg bw/day (nominal)
- Dose / conc.:
- 120 mg/kg bw/day (nominal)
- Dose / conc.:
- 330 mg/kg bw/day (nominal)
- No. of animals per sex per dose:
- ca 25
- Control animals:
- yes, concurrent vehicle
- Details on study design:
- Before the beginning of the treatment period, the females with confirmed mating were
allocated to the groups, according to a stratification procedure, so that the average body
weight of each group did not statistically differ. Females with the same day of gestation were
allocated to a different group.
Examinations
- Maternal examinations:
- Cage Side and Clinical Observations
All rats were observed twice daily, once in the morning and once in the afternoon at the same time,
for morbidity and mortality. Each female was also observed for signs of toxicity approximately 15-45
minutes following dose administration. In addition, the presence of findings at the time of dose
administration was recorded for individual animals.
Body Weights (F0)
Individual female body weights were recorded during animal identification, at day of confirmed mating
and group assignment (gestation day 0), on the first day of dose administration (gestation day 5), and
at three-day intervals thereafter (gestation days 8, 11, 14, 17, and 20 as the day of euthanasia). Body
weight value on gestation day 20 was corrected for gravid uterine weight to calculate maternal body
weight change.
Food Consumption
Food consumption was assessed for each female quantitatively as g/kg of body weight/day by
weighing of feeder (cage lid) at the beginning of the day and 24 hours after. Food consumption was
recorded prior to the initiation of dose administration (gestation days 0-1), and at three-day intervals
thereafter (gestation days 4-5, 7-8, 10-11, 13-14, 16-17 and 19-20).
Scheduled Euthanasia
On gestation day 20, all females were euthanized by anesthesia (Zoletil® / Xyla®, i.m.)
followed by terminal blood sampling for hormones assay and subjected
to hysterectomy.
The weight of the gravid uterus was recorded for each pregnant female (with at least one live
fetus). Uterus were examined. Ovaries were examined to determined number of corpora lutea.
Each dam was examined macroscopically, thyroid gland was collected in 10% neutral formalin
(in complex with trachea and esophagus) and weighed after fixation.
Necropsy of Females and Examination of Uterine Content
A complete necropsy was conducted on all females at scheduled termination. Necropsy
included examination of the external surface of the body, all orifices, the cranial cavity, the
external surface of the brain, and the thoracic, abdominal and pelvic cavities including viscera.
Hysterectomy and examination of uterine content was done for all females. Ovaries were
examined to determined number of corpora lutea. Gravid uterine weight was collected at
scheduled necropsy. Uteri, which appear non-gravid by macroscopic examination, were
opened and placed in 10 % ammonium sulfide solution for detection of early implantation loss.
Thyroid glands were preserved (in scheduled or euthanized in extremis females) and weighed
after fixation (scheduled euthanized).
Blood Sample Collection for Hormones Assay
Blood samples were collected from all surviving females at the scheduled necropsies
(as part of euthanasia on day 20 of post-mating).
Animals were not fasted prior to blood collection. The blood was collected terminally
following anesthesia (Zoletil® / XylaVET®) from the caudal vena cava after
laparotomy using a syringe with 23G needle. Blood collection was done on the first
part of the day (within 10:00 – 13:00 hours) in randomized order to avoid bias.
The blood sample was placed in a tube without anticoagulant. The blood was allowed
to clot for 50 min and centrifuged (1600 x g, 4 °C, 15 min) for serum separation.
Serum from each animal was divided into 6 aliquots (for two aliquots for each of T4,
T3 and TSH analysis) and immediately frozen at –70 °C until assayed.
T4, T3 and TSH Assay
Thyroid hormones (thyroxin (T4), triiodothyronine (T3), and thyroid stimulating
hormone (TSH)) were assayed in serum from all pregnant females (with at least one
fetus) by competitive inhibition enzyme immunoassay technique using relevant ELISA
kits (see below) and Multiskan™GO Microplate Spectrophotometer (Termo Scientific)
and according to standard procedure of manufacturer and SOP of BTL BIBC RAS.
Microscopic Examination of Thyroid Gland
Thyroid gland of all females euthanized at the scheduled necropsy was trimmed,
embedded in paraffin, sectioned, stained with hematoxylin and eosin, and examined
microscopically. - Ovaries and uterine content:
- The weight of the gravid uterus was recorded for each pregnant female (with at least one live
fetus). Uterus were examined. Ovaries were examined to determined number of corpora lutea.
Each dam was examined macroscopically, thyroid gland was collected in 10% neutral formalin
(in complex with trachea and esophagus) and weighed after fixation. - Fetal examinations:
- After cesarean section, all fetuses were subjected to external examination. Half of the fetuses
from each litter was examined for skeletal abnormalities and the remaining for soft tissue
alterations.
The fetal findings were described according to the harmonized terminology of the International
Federation of Teratology Societies (IFTS) [1, 2] without categorization and classified as
malformations or variations:
malformation (major abnormality) refers to structural change considered detrimental to the
animal (may also be lethal) and is usually rare;
variation (minor abnormality) refers to structural change considered to have little or no
detrimental effect on the animal; may be transient and may occur relatively frequently in
the control population.
The reproductive tract was examined with particular attention, and external sex was compared
with internal (gonadal) sex in all fetuses (examined for both skeletal and soft tissue
malformations). In addition, male fetuses were examined for undescended testes.
External Examination, Body Weight and AGD
Each live fetus was weighed and sexed with measurement of anogenital distance
(AGD). All fetuses were subjected to a detailed external examination for gross
anomalies with a recording of malformations and variations or non-classified findings.
Fetuses were then anaesthetized by subcutaneous injection of Zoletil® + XylaVET®
mixture and fixed in 96 % ethanol (approximately one-half of litter) for skeleton
examination or Bouin’s fixative (remainder of litter) for soft tissues examination.
Skeletal Examination
Approximately half of the live fetuses in each litter was fixed in ethyl alcohol,
eviscerated and skinned for subsequent double staining of cartilage and bone with
alcian blue and alizarin red.
A detailed examination of the skeleton was done and included the observation of all
the bone and cartilage structure of the head, spine, rib cage, pelvis, and limbs.
During evisceration, the reproductive tract was examined and external sex was
compared with internal (gonadal) sex; an indication of incomplete testicular descent
was noted in male fetuses.
Soft Tissues Examination
The remaining live fetuses in each litter were fixed with Bouin’s fluid. A detailed soft
tissue examination was performed according to a free-hand serial sectioning
technique, which will include the observation of all the organs and structures of the
head, neck, thorax and abdomen.
Organs within the abdomen were examined in unsectioned abdominal region with
particular attention on reproductive tract; an indication of incomplete testicular
descent was noted in male fetuses. - Statistics:
- All statistical tests were performed using Microsoft Excel (descriptive statistics) and statistical software
Statistica for Window v.7.1 to compare the treated groups to the control group. Descriptive statistics (mean,
standard deviation (S.D.), and N) are presented for all measurement data and shown in the summary
tables. The litter is accepted as an experimental unit for statistical analysis.
Continuous data variables (mean body weights and food consumption data) were analyzed by multi-factor
analysis of variance ANOVA-2, followed by the Duncan test, to determine inter-group differences. Former
implantation sites, number of corpora lutea, implantation loss indices, hormones concentration value,
uterine, and thyroid weights were analyzed by parametric one-way analysis of variance (ANOVA). If the
results of the ANOVA were significant (p<0.05), Dunnett's test is applied to the data to compare the treated
groups to the control group. The t-test was used additionally to compare each dose group with the control
value. Offspring sex ratio data, AGD value, and mean value of affected fetuses per litter were subjected to
the Kruskal-Wallis nonparametric ANOVA test to determine intergroup difference. If the results of the
ANOVA were significant (<0.05), Dunn's test is applied to the data to compare the treated groups to the
control group.
The fetal body weight was analyzed by sex as well as for both sexes combined using a one-way analysis of
variance (ANOVA) as described above. Additionally, statistical analysis for fetal body weight was done
using analysis of covariant with litter size as a covariant.
Descriptive data, percentage values, and pathomorphological data were analyzed by Fisher's Exact Test
and additionally by Chi-square test (when a tendency to a difference was observed). - Indices:
- Parameters Calculation / Note
Pregnant females alive at termination (N)
Body weight at necropsy (g)
Gravid uterine weight (abs, % of pregnant
female body weight)
Thyroid weight (abs, % of body weight without gravid uterine weight)
Females with total resorptions (N)
Females with all dead fetuses (N)
Females with live fetuses (N)
Corpora lutea (N per animal)
Implantation sites (N per animal)
Pre-implantation loss (N per animal, % of implantation sites) (Number of corpora lutea – Number of implantation sites) / Number of corpora lutea
Fetuses (N per animal)
Live fetuses (N per animal, % of implantation sites)
Dead fetuses (N per animal, % of implantation sites)
Resorptions + Scars (N per animal, % of implantation sites)
Implantation scars (N per animal, % of implantation sites)
Resorptions – early (N per animal, % of implantation sites)
Resorptions – late (N per animal, % of implantation sites)
Post-implantation loss (N per animal, % of implantation sites) (Number of implantation sites – Number of live fetuses) / Number of implantation sites - Historical control data:
- none reported
Results and discussion
Results: maternal animals
General toxicity (maternal animals)
- Clinical signs:
- effects observed, treatment-related
- Description (incidence and severity):
- The test item related clinical findings were observed in the 330 mg/kg bw/day dose group as follows: hypokinesia (12 females), staggering gait (11 females) or flatness as a more severe behavior disorder (6 females), excessive vocalization (2 females), chromodacryorrhea (2 females), ptyalism (2 females), nasal discharge (2 females); eyelid closure, hyphosis, and diarrhea was noted for single females.
These observations were episodic with the recovery of animals within approximately 1.5 – 3 hours after dosing. The higher frequency of clinical signs was noted after first dosing (gestation day 5), as well as at the end of the administration period (gestation days 14, 15, 17, and 19). Over the entire period of the test item administration, the total number of females with clinical findings in the 330 mg/kg bw/day dose group was 14 out of 26 examined (p < 0.001, Fisher Exact test).
In the 120 mg/kg bw/day dose group, one female (No. 18) had focal alopecia on the forelimbs observed beginning from day 9 of dosing, which supposed to be not test item related. - Dermal irritation (if dermal study):
- not examined
- Mortality:
- no mortality observed
- Description (incidence):
- There was no morbidity and mortality of females caused by the test item administration.
- Body weight and weight changes:
- effects observed, treatment-related
- Description (incidence and severity):
- The body weight of pregnant females administered with the dose of 330 mg/kg bw/day was slightly decreased compared to the control vehicle group at the gestation day 20 (by 5.0%, p < 0.05). The body weight gain in 330 mg/kg bw/day dose group was statistically reduced (p < 0.01) the entire period of administration compared with the control group as well as lower doses.
The reduced body weight gain of pregnant females in the 330 mg/kg bw/day dose group was associated with a smaller weight of the pregnant uterus (by 16 % compared to the control group, p < 0.05). The final maternal body weight without a gravid uterus did not statistically differ from the body weight of control females.
See Table S5 and S6 in 'Any other information on results incl tables' for details. - Food consumption and compound intake (if feeding study):
- no effects observed
- Description (incidence and severity):
- Mean food consumption in the 36, 120 and 330 mg/kg bw/day group was similar to that in the vehicle control group during all study days.
- 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
- Endocrine findings:
- no effects observed
- Description (incidence and severity):
- Thyroid Hormones Assay Data
Benzotriazole at the doses of 36, 120, and 330 mg/kg bw/day did not significantly affect the level of thyroid hormones (Thyroxine, Triiodothyronine, and Thyroid Stimulating Hormone) in the serum of pregnant females.
See Table S12 and S13 in 'Any other information on results incl tables' for more details. - 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):
- The absolute and relative thyroid weight of pregnant females was not significantly changed in all dose test item treated group.
See Tables S6 and S11 in 'Any other information on results incl tables' for details.
- Gross pathological findings:
- no effects observed
- Description (incidence and severity):
- All treated females were sacrificed during a scheduled necropsy on post-mating day 20.
During necropsy, there were no gross findings related to the test item administration. One female (No. 94) from the 330 mg/kg bw/day dose group had the uterus hydrometra, which is supposed to be not test item related.
Females No.38 (group 1), No.16, No.42, and No.56 (group 2), No.8, No.33, and No.94 (group 4) were without fetuses in the uterus. In female No.16, two early resorptions were revealed; there were no implantation sites, and scars were observed in non-pregnant females after staining of their’s uterus by ammonium sulfide.
See Tables S9 and S10 in 'Any other information on results incl tables' for details. - Neuropathological findings:
- not examined
- Histopathological findings: non-neoplastic:
- effects observed, treatment-related
- Description (incidence and severity):
- C-cell hyperplasia considered as test item related finding was observed in 3 of 24 females from 120 mg/kg bw/day dose group, and in 4 of 23 females from 330 mg/kg bw/day groups. C-cell hyperplasia was of minimum grade; however, it was not found in the control group, and the increase in occurrence in the high dose group was significant (p < 0.05, Fisher Exact test)
compared with the control group. Although there is no data on the serum level of calcitonin and calcium in pregnant females treated with benzotriazole, C-cell hyperplasia may be considered potentially adverse.
Remaining histological findings (congenital cysts, ectopic lymphoid tissue, and one finding of follicular cell vacuolization) were considered to be incidental not treatment-related findings.
See Table S12 in 'Any other information on results incl tables' for details. - Histopathological findings: neoplastic:
- no effects observed
Maternal developmental toxicity
- Number of abortions:
- no effects observed
- Description (incidence and severity):
- none reported - see Table S10 in 'Any other information on results incl tables' for more details.
- Pre- and post-implantation loss:
- effects observed, treatment-related
- Description (incidence and severity):
- The mean number of corpora lutea and pre-implantation loss did not statistically differ in the test item treated groups compared to the control vehicle group. The mean number of implantation sites was approximately the same among groups.
In the 120 and 330 mg/kg bw/day dose groups, the relative post-implantation loss was
increased compared to the control vehicle group (p < 0.01 and p < 0.05, respectively). The increase of post-implantation loss in these groups was associated with the increase in the absolute and percentage values of early resorptions. Also, the total number of females with post-implantation loss was increased (non-significantly) in the 120 and 330 mg/kg bw/day dose groups. The mean number of fetuses per female was slightly decreased in the 330 mg/kg bw/day dose group (by 6.2 % compared to the control group), but this change was not significant.
See Tables S9 and S10 in 'Any other information on results incl tables' for details. - Total litter losses by resorption:
- no effects observed
- Description (incidence and severity):
- no total litter loss was reported - see Table S10 in 'Any other information on results incl tables'
- Early or late resorptions:
- effects observed, treatment-related
- Description (incidence and severity):
- a significant difference in early resorptions is reported for the 120 and 330 mg/ kg bw/day dose group (p < 0.01 resp. p< 0.05) - - see Table S10 in 'Any other information on results incl tables'
- Dead fetuses:
- no effects observed
- Description (incidence and severity):
- none reported - - see Table S10 in 'Any other information on results incl tables'
- Changes in pregnancy duration:
- no effects observed
- Description (incidence and severity):
- none reported
- Changes in number of pregnant:
- no effects observed
- Description (incidence and severity):
- There was no difference in number of mated to number of pregnant females when compared to control group - see Table S10 in 'Any other information on results incl tables' for more details.
- Other effects:
- no effects observed
- Description (incidence and severity):
- no other effects reported
- Details on maternal toxic effects:
- maternal toxicity is noted
Effect levels (maternal animals)
- Key result
- Dose descriptor:
- NOAEL
- Effect level:
- 36 mg/kg bw/day (nominal)
- Based on:
- test mat.
- Basis for effect level:
- clinical signs
- histopathology: non-neoplastic
- pre and post implantation loss
Maternal abnormalities
- Abnormalities:
- effects observed, treatment-related
- Localisation:
- uterus
- Description (incidence and severity):
- increase in Post-implantation Loss.
Results (fetuses)
- Fetal body weight changes:
- effects observed, treatment-related
- Description (incidence and severity):
- In the 330 mg/kg bw/day dose group, body weight of male and female fetuses as well as mean fetuses weight of litter was significantly decreased compared to the control vehicle group (respectively, by 11.2 %, 11.8 %, and 11.5 %). See Table S14 in in 'Any other information on results incl tables' for more details.
- Reduction in number of live offspring:
- no effects observed
- Description (incidence and severity):
- See Table S10 in in 'Any other information on results incl tables' for more details.
- Changes in sex ratio:
- no effects observed
- Description (incidence and severity):
- The fetuses sex ratio in all dose treated groups was not significantly changed
compared to the control vehicle group. - Changes in litter size and weights:
- effects observed, treatment-related
- Description (incidence and severity):
- In the 330 mg/kg bw/day dose group, body weight of male and female fetuses as well as mean
fetuses weight of litter was significantly decreased compared to the control vehicle group
(respectively, by 11.2 %, 11.8 %, and 11.5 %). - Anogenital distance of all rodent fetuses:
- effects observed, treatment-related
- Description (incidence and severity):
- The absolute and normalized anogenital distance was not changed in male fetuses of all dose test item groups. For female fetuses, the normalized anogenital distance was statistically increased in the 330 mg/kg bw/day dose group.
- Changes in postnatal survival:
- not examined
- External malformations:
- effects observed, treatment-related
- Description (incidence and severity):
- There were no fetuses with external abnormalities recognized as malformations in the 36 mg/kg bw/day dose group.
In the 120 mg/kg bw/day dose group, three fetuses from one litter (No.90-2m, No. 90-3m and No. 90-4m) were with inward rotated hindlimbs. No skeletal and visceral malformations were observed for these fetuses; however, the altered ossifications and soft disintegrating consistency of skeleton can be noted for No.90-2m and No. 90-3m fetuses. Besides, these fetuses had a domed head as an external observation with unknown importance. In fetus No.90-4m, dilated ventricles of the brain were noted, which can be an associated finding. In the 120 mg/kg bw/day dose group, the increase in the incidence of brain ventricles dilation was noted (Section 11.5.3) during a visceral examination. However, in the 330 mg/kg bw/day dose
group, this alteration with unknown importance was not observed. Also, in 120 mg/kg bw/day dose group, there was no significant increase in fetal and litter incidence of skeletal observations, so these findings in one litter can be considered as with unclear relationship with the test item.
In the 330 mg/kg bw/day dose group, one fetus (52-7f) was with following malformations:
inward rotated hindlimbs, absent of some digits on the left hindlimb, thread-like tail, and absent of anus (confirmed during evisceration). This fetus also had a large abdomen, probably as a result of the absence of the anus. During evisceration, no other malformations of soft tissues were found. The external malformations in the fetus No. 52-7f were associated with the skeletal malformations (see Section 11.5.4), so the treatment relation of this finding cannot be excluded despite its uniqueness.
For the fetuses in 330 mg/kg bw/day dose group, an increase of small fetus in fetal and litter incidence was observed. This increase was not significant (p = 0.053, Fisher Exact test), however, correlated to the decrease in fetal body weight in this group, and considered as test-item related.
See Tables S15-1, S15-2, S16-1, S17-1, S17-2 in 'Any other information on results incl tables' for details. - Skeletal malformations:
- effects observed, treatment-related
- Description (incidence and severity):
- Skeletal malformations were found in one fetus (No.52-7f) from the 330 mg/kg bw/day group.
This fetus had no vertebrae after the thoracic T4, had only 7 ribs on the right and left, of which the 5th, 6th, and 7th pairs were unossified. During the external observation after the cesarean section, the few digits were recorded in the left hindpaw. Due to the low body weight of this fetus and soft consistency of limbs, the skin was not completely removed from the phalanges of hindlimbs to avoid damage and loss of structure during fetus processing. Phalanx cartilages of hindpaws were not stained appropriately; however, for left hindpaw, the absence of distal phalanges in 1st to 3d digits, absence of all phalanges in 4th digit, and absence of distal and medial phalanges in 5th digit are supposed; four metatarsals (Mt2-Mt5) were ossified. These
malformations were associated with external observations (thread-like tail). Despite the uniqueness of this case, it considered being test item-related.
Fetal skeletal variations which supposed to be related to the test item were observed in the 330 mg/kg bw/day dose group. The statistical significant increase in incidence. compared to the control vehicle group was noted for incomplete ossification of 2nd - 4th sternebra (fetal incidence, p < 0.05), unossification of 6th sternebra (fetal and litter incidence, p < 0.05), unossification in 5th metacarpal (fetal and litter incidence, p < 0.001 and p < 0.01) or its incomplete ossification (fetal incidence, p < 0.05).
The total affected fetuses with alteration in ossification was statistically increased for sternebra (fetal incidence, and mean of fetus per litter, p < 0.01), for metacarpal (fetal and litter incidence, and mean of fetus per litter, p < 0.01), and for total variations (fetal incidence, p < 0.001, and mean of fetus per litter, p < 0.01).
See Tables S15-1, S15-2, S17-1, S17-2 in 'Any other information on results incl tables' for details. - Visceral malformations:
- no effects observed
- Description (incidence and severity):
- No test item related malformations of fetal soft tissues were found. Findings of unilateral absent of pair organs (eye, and testis with epididymis and vas deferens) were considered as incidental, not test item related.
The statistical increase in the incidence of variations was observed in the 330 mg/kg bw/day dose group for the liver (discoloration - pale, spotted), kidney (discolored due to the hemorrhage), and uterus (thin uterine horns). The percentage increase was observed for the fetal incidence (liver and kidney), as well as for the litter incidence (kidney, uterus, and liver (non-significant)). Discoloration of renal pelvis content had a low incidence; however, it was associated with the hemorrhage in the kidney. The slight non-statistical dose-dependence was noted for these findings, so, they considered as test item related. It should be noted that thin uterine horns are regarded as of unknown importance and may be due to the small fetuses in the high dose group, recorded during an external examination and discussed above.
Alterations of unknown importance were observed in the 120 mg/kg bw/day dose group in the brain and kidney. The fetal and litter incidence of dilated brain ventricles was statistically increased compared to the control group as well as the dilated renal pelvis. In the 330 mg/kg bw/day dose group, the dilation of the fourth brain ventricle was found in 4 fetuses from 2 litters, and the dilation of the renal pelvis was found in 1 fetus, which did not significantly higher compared to the control group. So, the dilated brain ventricles and dilated renal pelvis in the 120 mg/kg bw/day dose group are considered to be with unclear relation to the test item administrations.
Other findings in soft tissues presented in Table S16-4 were recorded with approximately equal or/and low frequency in all groups and considered to be as not treatment-related. The fetal and litter incidence of testis malposition was the same in the test item treated and control groups. In most fetuses, this observation was expressed as a unilateral undescended testis at half the distance from the kidney.
The total affected fetuses (incidence value and mean per litter value) were not significantly changed in test item treated groups compared to the control vehicle group
See Tables S15-2, S16-1, S16-2, S16-3, S16-4 in 'Any other information on results incl tables' for details.. - Other effects:
- effects observed, treatment-related
- Description (incidence and severity):
- The fetuses sex ratio in all dose treated groups was not significantly changed compared to the control vehicle group.
- Details on embryotoxic / teratogenic effects:
- effects at 120 mg/kg bw/day are of unclear relation to the test item.
Therefore these effects are not considered for Effect level table below.
Effect levels (fetuses)
- Key result
- Dose descriptor:
- NOAEL
- Effect level:
- 120 mg/kg bw/day (nominal)
- Based on:
- test mat.
- Sex:
- male/female
- Basis for effect level:
- fetal/pup body weight changes
- changes in litter size and weights
- external malformations
- skeletal malformations
Fetal abnormalities
- Abnormalities:
- effects observed, treatment-related
- Localisation:
- external: anogenital distance
- skeletal: sternum
- other: fetus size
- Description (incidence and severity):
- incomplete or absent ossification in highest dose group
small fetuses in highest dose group
increased anogenital distance in female fetus in highest dose group
Overall developmental toxicity
- Developmental effects observed:
- yes
- Lowest effective dose / conc.:
- 330 mg/kg bw/day (nominal)
- Treatment related:
- yes
- Relation to maternal toxicity:
- not specified
- Dose response relationship:
- not specified
- Relevant for humans:
- not specified
Any other information on results incl. tables
TABLE S5 SUMMARY BODY WEIGHT AND BODY WEIGHT GAIN DATA FOR PREGNANT FEMALES
GROUP: | 1 (0 mg/kg) | 2 (36 mg/kg) | 3 (120 mg/kg) | 4 (330 mg/kg) |
| MEAN ± S.D. | MEAN ± S.D. | MEAN ± S.D. | MEAN ± S.D. |
| N=24 | N=21 | N=24 | N=23 |
Gestation day | Body weight, g | |||
0 | 210 ± 14 | 208 ± 12 | 210 ± 13 | 210 ± 15 |
5 | 233 ± 14 | 231 ± 14 | 233 ± 15 | 233 ± 16 |
8 | 242 ± 15 | 238 ± 13 | 239 ± 14 | 234 ± 13 |
11 | 256 ± 16 | 254 ± 15 | 253 ± 14 | 248 ± 14 |
14 | 269 ± 15 | 266 ± 16 | 267 ± 16 | 263 ± 15 |
17 | 299 ± 20 | 294 ± 19 | 295 ± 19 | 288 ± 17 |
20 | 342 ± 25 | 338 ± 24 | 337 ± 26 | 325 ± 22 (a) |
Period, gestation days | Body weight gain, % | |||
5-8 | 3.7 ± 1.7 | 3.3 ± 2.0 | 2.7 ± 2.0 | 0.7 ± 2.5 (b) |
5-11 | 9.6 ± 1.6 | 9.8 ± 1.9 | 8.8 ± 2.9 | 6.4 ± 2.5 (b) |
5-14 | 15.3 ± 2.1 | 15.3 ± 2.5 | 14.8 ± 3.2 | 12.2 ± 4.0 (b) |
5-17 | 27.9 ± 4.3 | 27.3 ± 2.7 | 26.7 ± 4.3 | 22.6 ± 6.3 (b) |
5-20 | 46.5 ± 6.3 | 46.2 ± 4.0 | 44.6 ± 7.1 | 37.5 ± 10.9 (b) |
(a) = Significantly different from control group 1 at 0.05 using repeated measures ANOVA Duncan test;
(b) = Significantly different from groups 1, 2 and 3 at 0.01 using repeated measures ANOVA Duncan test.
TABLE S6. SUMMARY DATA OF GRAVID UTERINE WEIGHT AND FINAL MATERNAL BODY WEIGHT
GROUP: | 1 (0 mg/kg) | 2 (36 mg/kg) | 3 (120 mg/kg) | 4 (330 mg/kg) |
| MEAN ± S.D. | MEAN ± S.D. | MEAN ± S.D. | MEAN ± S.D. |
| N=24 | N=21 | N=24 | N=23 |
Body weight at necropsy on gestation day 20, g | 339 ± 26 | 334 ± 24 | 334 ± 27 | 323 ± 22 (b) |
Gravid uterine weight, g | 71.2 ± 14.5 | 69.8 ± 10.0 | 68.2 ± 11.8 | 59.8 ± 15.1 (a) |
Final body weight without uterus, g | 267 ± 17 | 265 ± 19 | 265 ± 18 | 263 ± 16 |
(a) = Significantly different from control group 1 (0 mg/kg) at 0.05 using ANOVA Dunnet test;
(b) = Significantly different from control group 1 (0 mg/kg) at 0.05 using t-test.
TABLE S9. SUMMARY DATA OF CORPORA LUTEA NUMBER AND PRE-IMPLANTATION LOSS
GROUP: | 1 (0 mg/kg) | 2 (36 mg/kg) | 3 (120 mg/kg) | 4 (330 mg/kg) | ||||
Number of corpora lutea |
|
|
|
|
|
|
|
|
Total, N | 413 |
| 320 |
| 399 |
| 374 |
|
MEAN ± SD | 17.2 ± 3.5 | (N=24) | 15.2 ± 2.8 | (N=21) | 16.6 ± 2.8 | (N=24) | 16.3 ± 3.5 | (N=23) |
Number of implantation sites |
|
|
|
|
|
|
|
|
Total, N | 320 |
| 283 |
| 326 |
| 300 |
|
MEAN ± SD | 13.3 ± 2.8 | (N=24) | 13.5 ± 2.1 | (N=21) | 13.6 ± 2.3 | (N=24) | 13.0 ± 2.5 | (N=23) |
Pre-implantation loss |
|
|
|
|
|
|
|
|
Total, N | 93 |
| 37 |
| 73 |
| 74 |
|
MEAN ± SD | 3.9 ± 3.3 | (N=24) | 1.8 ± 1.6 | (N=21) | 3.0 ± 2.0 | (N=24) | 3.2 ± 3.9 | (N=23) |
% of corpora lutea | 22.5% |
| 11.6% |
| 18.3% |
| 19.8% |
|
TABLE S10. SUMMARY DATA OF UTERINE CONTENT
GROUP: | 1 (0 mg/kg) | 2 (36 mg/kg) | 3 (120 mg/kg) | 4 (330 mg/kg) | |
Number of treated females with confirmed mating | N | 25 | 24 | 24 | 26 |
Number of pregnant females | N | 24 | 21 | 24 | 23 |
Implantation sites | N | 320 | 283 | 326 | 300 |
No. per animal | MEAN ± SD | 13.3 ± 2.8 | 13.5 ± 2.1 | 13.6 ± 2.3 | 13.0 ± 2.5 |
Resorptions - Early | N | 7 | 5 | 21 | 18 |
% of implantation sites | 2.2 | 1.8 | 6.4 (a) | 6.0 (b) | |
No. per animal | MEAN ± SD | 0.3 ± 0.5 | 0.2 ± 0.5 | 0.9 ± 1.0 (c) | 0.8 ± 1.3 |
Resorptions - Late | N | 2 | 1 | 3 | 1 |
% of implantation sites | 0.6 | 0.4 | 0.9 | 0.4 | |
No. per animal | MEAN ± SD | 0.1 ± 0.3 | 0.0 ± 0.2 | 0.1 ± 0.4 | 0.0 ± 0.2 |
Post-implantation Loss | Total | 9 | 6 | 24 | 19 |
% of implantation sites | 2.8 | 2.1 | 7.4 (a) | 6.3 (b) | |
No. per animal | MEAN ± SD | 0.4 ± 0.6 | 0.3 ± 0.6 | 1.0 ± 1.1 (c) | 0.8 ± 1.3 |
|
|
|
|
|
|
Number of females with post-implantation loss | N / N pregnant | 8 / 24 | 5 / 21 | 13/24 | 11 / 23 |
|
|
|
|
|
|
Total Fetuses | N | 311 | 277 | 302 | 281 |
Alive | % | 100.0 | 100.0 | 100.0 | 100.0 |
Dead | % | 0.0 | 0.0 | 0.0 | 0.0 |
No. per animal | MEAN ± SD | 13.0 ± 2.7 | 13.2 ± 2.1 | 12.6 ± 2.7 | 12.2 ± 3.2 |
(a) Difference from control group 0 mg/kg/day with p < 0.01, Chi-square test;
(b) Difference from control group 0 mg/kg/day with p < 0.05, Chi-square test;
(c) Difference from control group 0 mg/kg/day with p < 0.05, Mann-Whitney test.
TABLE S11. SUMMARY DATA OF THYROIDS WEIGHT
GROUP: | 1 (0 mg/kg) | 2 (36 mg/kg) | 3 (120 mg/kg) | 4 (330 mg/kg) | ||||
MEAN ± S.D. | N | MEAN ± S.D. | N | MEAN ± S.D. | N | MEAN ± S.D. | N | |
Gravid body weight (a), g | 339 ± 26 | 24 | 334 ± 24 | 21 | 334 ± 27 | 24 | 323 ± 22 | 23 |
Body weight without uterus (b), g | 267 ± 17 | 24 | 265 ± 19 | 21 | 265 ± 18 | 24 | 263 ± 16 | 23 |
Thyroid weight |
|
|
|
|
|
|
|
|
Absolute weight, g | 0.0182 ± 0.0038 | 24 | 0.0172 ± 0.0034 | 21 | 0.0173 ± 0.0026 | 24 | 0.0171 ± 0.0023 | 23 |
Relative gravid body weight (a), g/100 g | 0.0054 ± 0.0011 | 24 | 0.0052 ± 0.0009 | 21 | 0.0052 ± 0.0008 | 24 | 0.0053 ± 0.0007 | 23 |
Relative body weight (b), g/100 g | 0.0068 ± 0.0013 | 24 | 0.0065 ± 0.0012 | 21 | 0.0065 ± 0.0009 | 24 | 0.0065 ± 0.0008 | 23 |
(a) Body weight of pregnant female at necropsy;
(b) Body weight without gravid uterine weight.
TABLE S12. SUMMARY DATA OF MICROSCOPIC FINDINGS IN THYROID GLANDS
GROUP: | 1 (0 mg/kg) | 2 (36 mg/kg) | 3 (120 mg/kg) | 4 (330 mg/kg) |
| N=24 | N=21 | N=24 | N=23 |
Finding, N |
|
|
|
|
C-cell hyperplasia | 0 | 0 | 3 | 4 (a) |
Minimal | 0 | 0 | 3 | 4 (a) |
Cyst, Congenital | 6 | 7 | 10 | 9 |
Minimal | 3 | 2 | 7 | 5 |
Slight | 3 | 5 | 3 | 4 |
Ectopic Lymphoid tissue | 2 | 2 | 2 | 1 |
Minimal | 2 | 1 | 1 | 0 |
Slight | 0 | 1 | 1 | 1 |
Follicular cell vacuolization, single follicle | 0 | 0 | 1 | 0 |
Minimal | 0 | 0 | 1 | 0 |
(a) Difference from control group 0 mg/kg/day with p < 0.05, Fisher Exact test
TABLE S13. SUMMARY DATA OF THYROID HORMONS SERUM LEVEL IN FEMALES
GROUP: | 1 (0 mg/kg) | 2 (36 mg/kg) | 3 (120 mg/kg) | 4 (330 mg/kg) | |||||
MEAN ± S.D. | N | MEAN ± S.D. | N | MEAN ± S.D. | N | MEAN ± S.D. | N | ||
Triiodothyronine (T3), ng/mL | 4.587 ± 1.284 | 24 | 4.897 ± 1.611 | 21 | 4.335 ± 1.394 | 24 | 4.321 ± 1.147 | 23 | |
Thyroxine (T4), ng/mL | 21.97 ± 6.06 | 24 | 19.15 ± 10.16 | 21 | 21.83 ± 8.10 | 24 | 25.16 ± 9.04 | 23 | |
Thyroid Stimulating Hormone (TSH), pg/mL | 472.2 ± 195.9 | 24 | 451.9 ± 167.2 | 20 | 442.5 ± 217.3 | 24 | 435.5 ± 194.8 | 23 | |
TABLE S14. SUMMARY RESULTS OF BODY WEIGHTS, ANOGENITAL DISTANCES AND SEX OF FETUSES
GROUP: | 1 (0 mg/kg) | 2 (36 mg/kg) | 3 (120 mg/kg) | 4 (330 mg/kg) | |
Number animals with fetuses |
| N=24 | N=21 | N=24 | N=23 |
Male Fetuses |
|
|
|
|
|
Body weight, g | MEAN ± SD | 3.74 ± 0.30 | 3.70 ± 0.20 | 3.82 ± 0.57 | 3.32 ± 0.30 (a) |
AGD, mm | MEAN ± SD | 2.61 ± 0.12 | 2.60 ± 0.12 | 2.61 ± 0.16 | 2.50 ± 0.20 |
AGD normalized | MEAN ± SD | 1.68 ± 0.07 | 1.68 ± 0.08 | 1.68 ± 0.11 | 1.67 ± 0.11 |
Number, total | N | 173 | 131 | 150 | 144 |
No. per animal | MEAN ± SD | 7.2 ± 1.8 | 6.2 ± 1.9 | 6.3 ± 1.8 | 6.3 ± 2.2 |
% males | % | 55.6 | 47.3 | 49.7 | 51.2 |
Female Fetuses |
| ||||
Body weight, g | MEAN ± SD | 3.56 ± 0.26 | 3.50 ± 0.14 | 3.65 ± 0.52 | 3.14 ± 0.29 (a) |
AGD, mm | MEAN ± SD | 1.07 ± 0.08 | 1.08 ± 0.07 | 1.08 ± 0.10 | 1.08 ± 0.08 |
AGD normalized | MEAN ± SD | 0.70 ± 0.05 | 0.71 ± 0.05 | 0.70 ± 0.07 | 0.74 ± 0.06 (b) |
Number, total | N | 138 | 146 | 152 | 137 |
No. per animal | MEAN ± SD | 5.8 ± 2.4 | 7.0 ± 1.7 | 6.3 ± 2.3 | 6.0 ± 2.5 |
% females | % | 44.4 | 52.7 | 50.3 | 48.8 |
Mean fetuses body weight, g | MEAN ± SD | 3.66 ± 0.28 | 3.59 ± 0.16 | 3.74 ± 0.54 | 3.24 ± 0.27 (c) |
(a) Significantly different from control group 1 at 0.001 using ANOVA Dunnett test;
(b) Difference from control group 0 mg/kg/day with p < 0.05, ANOVA Kruscal-Wallis test;
(c) Significantly different from control group 1 at 0.001 using ANOVA covariant test with litter size as a covariant.
TABLE S15-1. SUMMARY RESULTS OF FETUSES EXTERNAL MALFORMATIONS DATA
GROUP: | 1 (0 mg/kg) | 2 (36 mg/kg) | 3 (120 mg/kg) | 4 (330 mg/kg) | |
EXTERNAL MALFORMATIONS | |||||
Litters Evaluated | N | 24 | 21 | 24 | 23 |
Fetuses Evaluated |
| 311 | 277 | 302 | 281 |
Live | N | 311 | 277 | 302 | 281 |
Dead | N | 0 | 0 | 0 | 0 |
HINDLIMBS |
|
|
|
|
|
Malrotated, inward |
|
|
|
|
|
Fetal Incidence | N | 0 | 0 | 3 | 1 |
| % | 0.0 | 0.0 | 1.0 | 0.4 |
Litter Incidence | N | 0 | 0 | 1 | 1 |
| % | 0.0 | 0.0 | 4.2 | 4.3 |
Paw, Digits – Few |
|
|
|
|
|
Fetal Incidence | N | 0 | 0 | 0 | 1 |
| % | 0.0 | 0.0 | 0.0 | 0.4 |
Litter Incidence | N | 0 | 0 | 0 | 1 |
| % | 0.0 | 0.0 | 0.0 | 4.3 |
TAIL – Thread-like |
|
|
|
|
|
Fetal Incidence | N | 0 | 0 | 0 | 1 |
| % | 0.0 | 0.0 | 0.0 | 0.4 |
Litter Incidence | N | 0 | 0 | 0 | 1 |
| % | 0.0 | 0.0 | 0.0 | 4.3 |
TRUNK |
|
|
|
|
|
Anus - Absent |
|
|
|
|
|
Fetal Incidence | N | 0 | 0 | 0 | 1 |
| % | 0.0 | 0.0 | 0.0 | 0.4 |
Litter Incidence | N | 0 | 0 | 0 | 1 |
| % | 0.0 | 0.0 | 0.0 | 4.3 |
TOTAL AFFECTED FETUSES |
|
|
|
|
|
Fetal Incidence | N | 0 | 0 | 3 | 1 |
| % | 0.0 | 0.0 | 1.0 | 0.4 |
Litter Incidence | N | 0 | 0 | 1 | 1 |
| % | 0.0 | 0.0 | 4.2 | 4.3 |
Mean per litter, % | MEAN ± SD | 0.00 ± 0.00 | 0.00 ± 0.00 | 1.1 ± 5.6 | 0.3 ± 1.6 |
TABLE S15-2. SUMMARY RESULTS OF FETUSES VARIATIONS AND OTHER OBSERVATION DATA
GROUP: | 1 (0 mg/kg) | 2 (36 mg/kg) | 3 (120 mg/kg) | 4 (330 mg/kg) | |
EXTERNAL VARIATIONS AND OTHER OBSERVATIONS | |||||
Litters Evaluated | N | 24 | 21 | 24 | 23 |
Fetuses Evaluated |
| 311 | 277 | 302 | 281 |
Live | N | 311 | 277 | 302 | 281 |
Dead | N | 0 | 0 | 0 | 0 |
GENERAL |
|
|
|
|
|
Subcutaneous hemorrhage |
|
|
|
|
|
Fetal Incidence | N | 58 | 41 | 52 | 42 |
| % | 18.6 | 14.8 | 17.2 | 14.9 |
Litter Incidence | N | 17 | 19 | 16 | 18 |
| % | 70.8 | 90.5 | 66.7 | 78.3 |
Intraperitoneal hemorrhage |
|
|
|
|
|
Fetal Incidence | N | 0 | 1 | 0 | 0 |
| % | 0.0 | 0.4 | 0.0 | 0.0 |
Litter Incidence | N | 0 | 1 | 0 | 0 |
| % | 0.0 | 4.8 | 0.0 | 0.0 |
Fetus - Small |
|
|
|
|
|
Fetal Incidence | N | 2 | 0 | 3 | 8 |
| % | 0.6 | 0.0 | 1.0 | 2.8 |
Litter Incidence | N | 2 | 0 | 3 | 4 |
| % | 8.3 | 0.0 | 12.5 | 17.4 |
Fetus - Pale |
|
|
|
|
|
Fetal Incidence | N | 1 | 0 | 0 | 1 |
| % | 0.3 | 0.0 | 0.0 | 0.4 |
Litter Incidence | N | 1 | 0 | 0 | 1 |
| % | 4.2 | 0.0 | 0.0 | 4.3 |
HEAD/NECK |
|
|
|
|
|
Domed head |
|
|
|
|
|
Fetal Incidence | N | 0 | 0 | 3 | 0 |
| % | 0.0 | 0.0 | 1.0 | 0.0 |
Litter Incidence | N | 0 | 0 | 1 | 0 |
| % | 0.0 | 0.0 | 4.2 | 0.0 |
TRUNK | % |
|
|
|
|
Genital Tubercle- Large |
|
|
|
|
|
Fetal Incidence | N | 6 | 2 | 1 | 6 |
| % | 1.9 | 0.7 | 0.3 | 2.1 |
Litter Incidence | N | 2 | 2 | 1 | 3 |
| % | 8.3 | 9.5 | 4.2 | 13.0 |
Abdomen - Enlarged |
|
|
|
|
|
Fetal Incidence | N | 0 | 0 | 0 | 1 |
| % | 0.0 | 0.0 | 0.0 | 0.4 |
Litter Incidence | N | 0 | 0 | 0 | 1 |
| % | 0.0 | 0.0 | 0.0 | 4.3 |
TOTAL AFFECTED FETUSES |
|
|
|
|
|
Fetal Incidence | N | 64 | 44 | 54 | 53 |
| % | 20.6 | 15.9 | 17.9 | 18.9 |
Litter Incidence | N | 19 | 20 | 17 | 20 |
| % | 79.2 | 95.2 | 70.8 | 87.0 |
Mean per litter, % | MEAN ± SD | 19.3 ± 15.9 | 15.7 ± 12.4 | 16.5 ± 14.3 | 19.6 ± 13.5 |
TABLE S16-1. SUMMARY DATA OF FETAL SOFT TISSUE MALFORMATIONS
GROUP: | 1 (0 mg/kg) | 2 (36 mg/kg) | 3 (120 mg/kg) | 4 (330 mg/kg) | |
Litters Evaluated | N | 24 | 21 | 24 | 23 |
Fetuses Evaluated | N | 153 | 138 | 149 | 139 |
Males | N | 89 | 67 | 81 | 75 |
Females | N | 64 | 71 | 68 | 64 |
|
|
|
|
|
|
EYE – ABSENT (unilateral) |
|
|
|
|
|
Fetal Incidence | N | 0 | 0 | 0 | 1 |
| % | 0.0 | 0.0 | 0.0 | 0.7 |
Litter Incidence | N | 0 | 0 | 0 | 1 |
| % | 0.0 | 0.0 | 0.0 | 4.3 |
Affected fetuses per Litter | MEAN% | 0.0 | 0.0 | 0.0 | 0.6 |
| SD | 0.0 | 0.0 | 0.0 | 3.0 |
|
|
|
|
|
|
TESTIS – ABSENT (unilateral) |
|
|
|
| |
Fetal Incidence | N | 1 | 0 | 1 | 0 |
| % | 1.1 | 0.0 | 1.2 | 0.0 |
Litter Incidence | N | 1 | 0 | 1 | 0 |
| % | 4.2 | 0.0 | 4.2 | 0.0 |
Affected fetuses per Litter | MEAN% | 0.6 | 0.0 | 1.0 | 0.0 |
| SD | 2.9 | 0.0 | 5.1 | 0.0 |
|
|
|
|
|
|
EPIDIDYMIS – ABSENT (unilateral) |
|
|
|
| |
Fetal Incidence | N | 1 | 0 | 1 | 0 |
| % | 1.1 | 0.0 | 1.2 | 0.0 |
Litter Incidence | N | 1 | 0 | 1 | 0 |
| % | 4.2 | 0.0 | 4.2 | 0.0 |
Affected fetuses per Litter | MEAN% | 0.6 | 0.0 | 1.0 | 0.0 |
| SD | 2.9 | 0.0 | 5.1 | 0.0 |
|
|
|
|
|
|
VAS DEFERENS – ABSENT (unilateral) |
|
|
|
| |
Fetal Incidence | N | 1 | 0 | 1 | 0 |
| % | 1.1 | 0.0 | 1.2 | 0.0 |
Litter Incidence | N | 1 | 0 | 1 | 0 |
| % | 4.2 | 0.0 | 4.2 | 0.0 |
Affected fetuses per Litter | MEAN% | 0.6 | 0.0 | 1.0 | 0.0 |
| SD | 2.9 | 0.0 | 5.1 | 0.0 |
TABLE S16-2. SUMMARY DATA OF FETAL SOFT TISSUE VARIATIONS AND OTHER ALTERATIONS: FINDINGS ARE CONSIDERED TO BE ASSOCIATED WITH ADMINISTRATION OF THE TEST ITEM
| GROUP: | 1 (0 mg/kg) | 2 (36 mg/kg) | 3 (120 mg/kg) | 4 (330 mg/kg) | |
| Litters Evaluated | N | 24 | 21 | 24 | 23 |
| Fetuses Evaluated | N | 153 | 138 | 149 | 139 |
| Males | N | 89 | 67 | 81 | 75 |
| Females | N | 64 | 71 | 68 | 64 |
| LIVER |
|
|
|
|
|
LIVER LOBE - Discolored (pale, spots) |
|
|
|
|
| |
Fetal Incidence | N | 2 | 2 | 4 | 12 | |
| % | 1.3 | 1.4 | 2.7 | 8.6 (a) | |
Litter Incidence | N | 2 | 2 | 3 | 6 | |
| % | 8.3 | 9.5 | 12.5 | 26.1 | |
Affected fetuses per Litter | MEAN% | 1.4 | 1.4 | 2.9 | 7.3 | |
| SD | 4.7 | 4.3 | 8.9 | 18.5 | |
| KIDNEY |
|
|
|
|
|
KIDNEY - Discolored (hemorrhage) |
|
|
|
| ||
Fetal Incidence | N | 1 | 0 | 4 | 9 | |
| % | 0.7 | 0.0 | 2.7 | 6.5 (a) | |
Litter Incidence | N | 1 | 0 | 4 | 6 | |
| % | 4.2 | 0.0 | 16.7 | 26.1 (b) | |
Affected fetuses per Litter | MEAN% | 0.5 | 0.0 | 2.5 | 7.0 | |
| SD | 2.6 | 0.0 | 5.9 | 13.9 | |
RENAL PELVIS CONTENT - Discolored |
|
|
|
| ||
Fetal Incidence | N | 0 | 0 | 0 | 2 | |
| % | 0.0 | 0.0 | 0.0 | 1.4 | |
Litter Incidence | N | 0 | 0 | 0 | 2 | |
| % | 0.0 | 0.0 | 0.0 | 8.7 | |
Affected fetuses per Litter | MEAN% | 0.0 | 0.0 | 0.0 | 2.8 | |
| SD | 0.0 | 0.0 | 0.0 | 10.7 | |
| UTERUS |
|
|
|
|
|
UTERINE HORNS - Thin |
|
|
|
| ||
Fetal Incidence | N | 0 | 2 | 2 | 4 | |
| % | 0.0 | 2.8 | 2.9 | 6.3 | |
Litter Incidence | N | 0 | 2 | 2 | 4 | |
| % | 0.0 | 9.5 | 8.3 | 17.4 (b) | |
Affected fetuses per Litter | MEAN% | 0.0 | 3.6 | 2.4 | 6.5 | |
| SD | 0.0 | 12.0 | 8.3 | 15.5 | |
(a) Significantly different from control group 1 at 0.01 using Fisher Exact test;
(b) Significantly different from control group 1 at 0.05 using Fisher Exact test
TABLE S16-3. SUMMARY DATA OF FETAL SOFT TISSUE VARIATIONS AND OTHER ALTERATIONS: FINDINGS OF UNCLEAR RELATION TO THE TEST ITEM ADMINISTRATION
| GROUP: | 1 (0 mg/kg) | 2 (36 mg/kg) | 3 (120 mg/kg) | 4 (330 mg/kg) | |
| Litters Evaluated | N | 24 | 21 | 24 | 23 |
| Fetuses Evaluated | N | 153 | 138 | 149 | 139 |
| Males | N | 89 | 67 | 81 | 75 |
| Females | N | 64 | 71 | 68 | 64 |
| BRAIN |
|
|
|
|
|
| FOURTH VENTRICLE - Dilated |
|
|
|
| |
| Fetal Incidence | N | 0 | 0 | 8 | 0 |
|
| % | 0.0 | 0.0 | 5.4 (a) | 0.0 |
| Litter Incidence | N | 0 | 0 | 4 | 0 |
|
| % | 0.0 | 0.0 | 16.7 (b) | 0.0 |
| Affected fetuses per Litter | MEAN% | 0.0 | 0.0 | 4.8 | 0.0 |
|
| SD | 0.0 | 0.0 | 12.4 | 0.0 |
| LATERAL VENTRICLE - Dilated |
|
|
|
| |
| Fetal Incidence | N | 1 | 0 | 8 | 4 |
|
| % | 0.7 | 0.0 | 5.4 (b) | 2.9 |
| Litter Incidence | N | 1 | 0 | 4 | 2 |
|
| % | 4.2 | 0.0 | 16.7 | 8.7 |
| Affected fetuses per Litter | MEAN% | 0.5 | 0.0 | 5.0 | 3.3 |
|
| SD | 2.6 | 0.0 | 15.2 | 11.1 |
| THIRD VENTRICLE - Dilated |
|
|
|
| |
| Fetal Incidence | N | 0 | 0 | 5 | 0 |
|
| % | 0.0 | 0.0 | 3.4 (b) | 0.0 |
| Litter Incidence | N | 0 | 0 | 4 | 0 |
|
| % | 0.0 | 0.0 | 16.7 (b) | 0.0 |
| Affected fetuses per Litter | MEAN% | 0.0 | 0.0 | 3.2 | 0.0 |
|
| SD | 0.0 | 0.0 | 7.7 | 0.0 |
| VENTRICLE - Dilated |
|
|
|
|
|
| Fetal Incidence | N | 0 | 0 | 5 | 0 |
|
| % | 0.0 | 0.0 | 3.4 (a) | 0.0 |
| Litter Incidence | N | 0 | 0 | 5 | 0 |
|
| % | 0.0 | 0.0 | 20.8 (a) | 0.0 |
| Affected fetuses per Litter | MEAN% | 0.0 | 0.0 | 3.4 | 0.0 |
|
| SD | 0.0 | 0.0 | 7.2 | 0.0 |
| KIDNEY |
|
|
|
|
|
RENAL PELVIS - Dilated |
|
|
|
| ||
Fetal Incidence | N | 2 | 6 | 10 | 1 | |
| % | 1.3 | 4.3 | 6.7 (b) | 0.7 | |
Litter Incidence | N | 2 | 4 | 8 | 1 | |
| % | 8.3 | 19.0 | 33.3 (a) | 4.3 | |
Affected fetuses per Litter | MEAN% | 1.5 | 4.9 | 7.0 | 0.6 | |
| SD | 5.2 | 13.7 | 12.1 | 3.0 | |
(a) Significantly different from control group 1 at 0.01 using Fisher Exact test;
(b) Significantly different from control group 1 at 0.05 using Fisher Exact test
TABLE S16-4. SUMMARY DATA OF FETAL SOFT TISSUE VARIATIONS AND OTHER ALTERATIONS: FINDINGS WERE NOT CONSIDERED TO BE ASSOCIATED WITH ADMINISTRATION OF THE TEST ITEM
GROUP: | 1 (0 mg/kg) | 2 (36 mg/kg) | 3 (120 mg/kg) | 4 (330 mg/kg) | |
Litters Evaluated | N | 24 | 21 | 24 | 23 |
Fetuses Evaluated | N | 153 | 138 | 149 | 139 |
Males | N | 89 | 67 | 81 | 75 |
Females | N | 64 | 71 | 68 | 64 |
ABDOMEN-Intra-abdominal hemorrhage |
|
|
|
|
|
Fetal Incidence | N | 7 | 13 | 11 | 7 |
| % | 4.6 | 9.4 | 7.4 | 5.0 |
Litter Incidence | N | 5 | 7 | 3 | 7 |
| % | 20.8 | 33.3 | 12.5 | 30.4 |
Affected fetuses per Litter | MEAN% | 4.0 | 9.1 | 8.5 | 6.3 |
| SD | 9.2 | 14.3 | 23.7 | 12.0 |
BRAIN |
|
|
|
| |
CEREBELLUM - Red material |
|
|
|
| |
Fetal Incidence | N | 0 | 1 | 0 | 1 |
| % | 0.0 | 0.7 | 0.0 | 0.7 |
Litter Incidence | N | 0 | 1 | 0 | 1 |
| % | 0.0 | 4.8 | 0.0 | 4.3 |
Affected fetuses per Litter | MEAN% | 0.0 | 0.7 | 0.0 | 0.5 |
| SD | 0.0 | 3.1 | 0.0 | 2.6 |
OLFACTORY LOBE - Large (unilateral) |
|
|
|
| |
Fetal Incidence | N | 0 | 1 | 0 | 1 |
| % | 0.0 | 0.7 | 0.0 | 0.7 |
Litter Incidence | N | 0 | 1 | 0 | 1 |
| % | 0.0 | 4.8 | 0.0 | 4.3 |
Affected fetuses per Litter | MEAN% | 0.0 | 0.7 | 0.0 | 0.6 |
| SD | 0.0 | 3.1 | 0.0 | 3.0 |
PERIMENINGEAL SPACE - Red material |
|
|
|
| |
Fetal Incidence | N | 12 | 3 | 10 | 7 |
| % | 7.8 | 2.2 | 6.7 | 5.0 |
Litter Incidence | N | 8 | 3 | 6 | 4 |
| % | 33.3 | 14.3 | 25.0 | 17.4 |
Affected fetuses per Litter | MEAN% | 8.9 | 2.4 | 7.6 | 5.8 |
| SD | 15.2 | 6.2 | 15.7 | 16.7 |
EAR, Inner/Middle - Red material |
|
|
|
| |
Fetal Incidence | N | 3 | 4 | 5 | 3 |
| % | 2.0 | 2.9 | 3.4 | 2.2 |
Litter Incidence | N | 3 | 4 | 5 | 3 |
| % | 12.5 | 19.0 | 20.8 | 13.0 |
Affected fetuses per Litter | MEAN% | 1.8 | 2.9 | 3.6 | 2.0 |
| SD | 4.9 | 6.1 | 7.3 | 5.2 |
TABLE S16-4. SUMMARY DATA OF FETAL SOFT TISSUE VARIATIONS AND OTHER ALTERATIONS: FINDINGS WERE NOT CONSIDERED TO BE ASSOCIATED WITH ADMINISTRATION OF THE TEST ITEM, CONTINUATION
GROUP: | 1 (0 mg/kg) | 2 (36 mg/kg) | 3 (120 mg/kg) | 4 (330 mg/kg) | |
Litters Evaluated | N | 24 | 21 | 24 | 23 |
Fetuses Evaluated | N | 153 | 138 | 149 | 139 |
Males | N | 89 | 67 | 81 | 75 |
Females | N | 64 | 71 | 68 | 64 |
HEART |
|
|
|
|
|
ATRIUM - Discolored (pale) |
|
|
|
| |
Fetal Incidence | N | 0 | 1 | 0 | 1 |
| % | 0.0 | 0.7 | 0.0 | 0.7 |
Litter Incidence | N | 0 | 1 | 0 | 1 |
| % | 0.0 | 4.8 | 0.0 | 4.3 |
Affected fetuses per Litter | MEAN% | 0.0 | 0.7 | 0.0 | 0.5 |
| SD | 0.0 | 3.1 | 0.0 | 2.6 |
ATRIUM - Large |
|
|
|
| |
Fetal Incidence | N | 0 | 1 | 0 | 0 |
| % | 0.0 | 0.7 | 0.0 | 0.0 |
Litter Incidence | N | 0 | 1 | 0 | 0 |
| % | 0.0 | 4.8 | 0.0 | 0.0 |
Affected fetuses per Litter | MEAN% | 0.0 | 0.7 | 0.0 | 0.0 |
| SD | 0.0 | 3.1 | 0.0 | 0.0 |
ATRIUM - Small |
|
|
|
| |
Fetal Incidence | N | 0 | 0 | 1 | 0 |
| % | 0.0 | 0.0 | 0.7 | 0.0 |
Litter Incidence | N | 0 | 0 | 1 | 0 |
| % | 0.0 | 0.0 | 4.2 | 0.0 |
Affected fetuses per Litter | MEAN% | 0.0 | 0.0 | 0.8 | 0.0 |
| SD | 0.0 | 0.0 | 4.1 | 0.0 |
PERICARDIUM - Blood filled |
|
|
|
| |
Fetal Incidence | N | 4 | 0 | 3 | 0 |
| % | 2.6 | 0.0 | 2.0 | 0.0 |
Litter Incidence | N | 1 | 0 | 3 | 0 |
| % | 4.2 | 0.0 | 12.5 | 0.0 |
Affected fetuses per Litter | MEAN% | 2.8 | 0.0 | 2.1 | 0.0 |
| SD | 13.6 | 0.0 | 5.8 | 0.0 |
VENTRICLES - Dilated, Blood-filled |
|
|
|
| |
Fetal Incidence | N | 15 | 10 | 9 | 11 |
| % | 9.8 | 7.2 | 6.0 | 7.9 |
Litter Incidence | N | 4 | 6 | 5 | 4 |
| % | 16.7 | 28.6 | 20.8 | 17.4 |
Affected fetuses per Litter | MEAN% | 9.6 | 7.6 | 5.5 | 6.9 |
| SD | 25.0 | 13.9 | 13.8 | 19.0 |
VENTRICLE WALL - Discolored |
|
|
|
|
|
Fetal Incidence | N | 0 | 0 | 3 | 0 |
| % | 0.0 | 0.0 | 2.0 | 0.0 |
Litter Incidence | N | 0 | 0 | 1 | 0 |
| % | 0.0 | 0.0 | 4.2 | 0.0 |
Affected fetuses per Litter | MEAN% | 0.0 | 0.0 | 2.5 | 0.0 |
| SD | 0.0 | 0.0 | 12.2 | 0.0 |
TABLE S16-4. SUMMARY DATA OF FETAL SOFT TISSUE VARIATIONS AND OTHER ALTERATIONS: FINDINGS WERE NOT CONSIDERED TO BE ASSOCIATED WITH ADMINISTRATION OF THE TEST ITEM, CONTINUATION
GROUP: | 1 (0 mg/kg) | 2 (36 mg/kg) | 3 (120 mg/kg) | 4 (330 mg/kg) | |
Litters Evaluated | N | 24 | 21 | 24 | 23 |
Fetuses Evaluated | N | 153 | 138 | 149 | 139 |
Males | N | 89 | 67 | 81 | 75 |
Females | N | 64 | 71 | 68 | 64 |
AORTA - Dilated |
|
|
|
| |
Fetal Incidence | N | 0 | 1 | 0 | 0 |
| % | 0.0 | 0.7 | 0.0 | 0.0 |
Litter Incidence | N | 0 | 1 | 0 | 0 |
| % | 0.0 | 4.8 | 0.0 | 0.0 |
Affected fetuses per Litter | MEAN% | 0.0 | 0.7 | 0.0 | 0.0 |
| SD | 0.0 | 3.1 | 0.0 | 0.0 |
CAROTID ARTERY - Dilated |
|
|
|
|
|
Fetal Incidence | N | 0 | 0 | 1 | 0 |
| % | 0.0 | 0.0 | 0.7 | 0.0 |
Litter Incidence | N | 0 | 0 | 1 | 0 |
| % | 0.0 | 0.0 | 4.2 | 0.0 |
Affected fetuses per Litter | MEAN% | 0.0 | 0.0 | 0.6 | 0.0 |
| SD | 0.0 | 0.0 | 2.9 | 0.0 |
VEIN, HEPATIC - Dilated |
|
|
|
| |
Fetal Incidence | N | 5 | 3 | 3 | 7 |
| % | 3.3 | 2.2 | 2.0 | 5.0 |
Litter Incidence | N | 3 | 1 | 2 | 4 |
| % | 12.5 | 4.8 | 8.3 | 17.4 |
Affected fetuses per Litter | MEAN% | 3.3 | 2.0 | 2.0 | 4.4 |
| SD | 9.6 | 9.4 | 7.0 | 8.8 |
VEIN, CAUDAL - Dilated |
|
|
|
| |
Fetal Incidence | N | 0 | 1 | 1 | 0 |
| % | 0.0 | 0.7 | 0.7 | 0.0 |
Litter Incidence | N | 0 | 1 | 1 | 0 |
| % | 0.0 | 4.8 | 4.2 | 0.0 |
Affected fetuses per Litter | MEAN% | 0.0 | 1.0 | 0.6 | 0.0 |
| SD | 0.0 | 4.4 | 2.9 | 0.0 |
VEIN, RENAL - Dilated |
|
|
|
| |
Fetal Incidence | N | 3 | 0 | 2 | 5 |
| % | 2.0 | 0.0 | 1.3 | 3.6 |
Litter Incidence | N | 2 | 0 | 1 | 2 |
| % | 8.3 | 0.0 | 4.2 | 8.7 |
Affected fetuses per Litter | MEAN% | 1.9 | 0.0 | 1.7 | 4.1 |
| SD | 7.2 | 0.0 | 8.2 | 13.6 |
TABLE S16-4. SUMMARY DATA OF FETAL SOFT TISSUE VARIATIONS AND OTHER ALTERATIONS: FINDINGS WERE NOT CONSIDERED TO BE ASSOCIATED WITH ADMINISTRATION OF THE TEST ITEM, CONTINUATION
GROUP: | 1 (0 mg/kg) | 2 (36 mg/kg) | 3 (120 mg/kg) | 4 (330 mg/kg) | |
Litters Evaluated | N | 24 | 21 | 24 | 23 |
Fetuses Evaluated | N | 153 | 138 | 149 | 139 |
Males | N | 89 | 67 | 81 | 75 |
Females | N | 64 | 71 | 68 | 64 |
LIVER |
|
|
|
|
|
LIVER LOBE - Discolored (hemorrhage) |
|
|
|
|
|
Fetal Incidence | N | 5 | 3 | 4 | 2 |
| % | 3.3 | 2.2 | 2.7 | 1.4 |
Litter Incidence | N | 5 | 3 | 2 | 2 |
| % | 20.8 | 14.3 | 8.3 | 8.7 |
Affected fetuses per Litter | MEAN% | 3.1 | 2.1 | 2.9 | 1.4 |
| SD | 6.2 | 5.2 | 9.8 | 4.8 |
LIVER LOBE, Vessels - Dilated |
|
|
|
| |
Fetal Incidence | N | 1 | 0 | 1 | 0 |
| % | 0.7 | 0.0 | 0.7 | 0.0 |
Litter Incidence | N | 1 | 0 | 1 | 0 |
| % | 4.2 | 0.0 | 4.2 | 0.0 |
Affected fetuses per Litter | MEAN% | 0.7 | 0.0 | 0.6 | 0.0 |
| SD | 3.4 | 0.0 | 2.9 | 0.0 |
BILE DUCT - Dilated |
|
|
|
| |
Fetal Incidence | N | 0 | 0 | 1 | 1 |
| % | 0.0 | 0.0 | 0.7 | 0.7 |
Litter Incidence | N | 0 | 0 | 1 | 1 |
| % | 0.0 | 0.0 | 4.2 | 4.3 |
Affected fetuses per Litter | MEAN% | 0.0 | 0.0 | 0.6 | 0.5 |
| SD | 0.0 | 0.0 | 2.9 | 2.3 |
STOMACH, WALL - Alteration of texture |
|
|
|
| |
Fetal Incidence | N | 0 | 0 | 4 | 0 |
| % | 0.0 | 0.0 | 2.7 | 0.0 |
Litter Incidence | N | 0 | 0 | 1 | 0 |
| % | 0.0 | 0.0 | 4.2 | 0.0 |
Affected fetuses per Litter | MEAN% | 0.0 | 0.0 | 3.3 | 0.0 |
| SD | 0.0 | 0.0 | 16.3 | 0.0 |
STOMACH, WALL - Discoloration |
|
|
|
| |
Fetal Incidence | N | 0 | 0 | 3 | 0 |
| % | 0.0 | 0.0 | 2.0 | 0.0 |
Litter Incidence | N | 0 | 0 | 1 | 0 |
| % | 0.0 | 0.0 | 4.2 | 0.0 |
Affected fetuses per Litter | MEAN% | 0.0 | 0.0 | 2.5 | 0.0 |
| SD | 0.0 | 0.0 | 12.2 | 0.0 |
PANCREAS - Discolored (dark) |
|
|
|
| |
Fetal Incidence | N | 1 | 1 | 0 | 1 |
| % | 0.7 | 0.7 | 0.0 | 0.7 |
Litter Incidence | N | 1 | 1 | 0 | 1 |
| % | 4.2 | 4.8 | 0.0 | 4.3 |
Affected fetuses per Litter | MEAN% | 0.5 | 0.6 | 0.0 | 0.5 |
| SD | 2.6 | 2.7 | 0.0 | 2.6 |
TABLE S16-4. SUMMARY DATA OF FETAL SOFT TISSUE VARIATIONS AND OTHER ALTERATIONS: FINDINGS WERE NOT CONSIDERED TO BE ASSOCIATED WITH ADMINISTRATION OF THE TEST ITEM, CONTINUATION
GROUP: | 1 (0 mg/kg) | 2 (36 mg/kg) | 3 (120 mg/kg) | 4 (330 mg/kg) | |
Litters Evaluated | N | 24 | 21 | 24 | 23 |
Fetuses Evaluated | N | 153 | 138 | 149 | 139 |
Males | N | 89 | 67 | 81 | 75 |
Females | N | 64 | 71 | 68 | 64 |
SPLEEN - Discolored (dark) |
|
|
|
|
|
Fetal Incidence | N | 1 | 0 | 0 | 1 |
| % | 0.7 | 0.0 | 0.0 | 0.7 |
Litter Incidence | N | 1 | 0 | 0 | 1 |
| % | 4.2 | 0.0 | 0.0 | 4.3 |
Affected fetuses per Litter | MEAN% | 0.5 | 0.0 | 0.0 | 0.5 |
| SD | 2.6 | 0.0 | 0.0 | 2.6 |
INTESTINE WALL - Discolored (dark) |
|
|
|
| |
Fetal Incidence | N | 0 | 2 | 4 | 0 |
| % | 0.0 | 1.4 | 2.7 | 0.0 |
Litter Incidence | N | 0 | 2 | 2 | 0 |
| % | 0.0 | 9.5 | 8.3 | 0.0 |
Affected fetuses per Litter | MEAN% | 0.0 | 1.3 | 3.1 | 0.0 |
| SD | 0.0 | 4.0 | 12.5 | 0.0 |
INTESTINE WALL - Alteration of texture |
|
|
|
|
|
Fetal Incidence | N | 0 | 0 | 3 | 0 |
| % | 0.0 | 0.0 | 2.0 | 0.0 |
Litter Incidence | N | 0 | 0 | 1 | 0 |
| % | 0.0 | 0.0 | 4.2 | 0.0 |
Affected fetuses per Litter | MEAN% | 0.0 | 0.0 | 2.5 | 0.0 |
| SD | 0.0 | 0.0 | 12.2 | 0.0 |
KIDNEY |
|
|
|
|
|
RENAL PAPILLA - Small |
|
|
|
| |
Fetal Incidence | N | 2 | 1 | 4 | 1 |
| % | 1.3 | 0.7 | 2.7 | 0.7 |
Litter Incidence | N | 2 | 1 | 4 | 1 |
| % | 8.3 | 4.8 | 16.7 | 4.3 |
Affected fetuses per Litter | MEAN% | 1.5 | 0.7 | 2.6 | 0.6 |
| SD | 5.2 | 3.1 | 6.2 | 3.0 |
RENAL PELVIS - Small |
|
|
|
| |
Fetal Incidence | N | 2 | 0 | 0 | 0 |
| % | 1.3 | 0.0 | 0.0 | 0.0 |
Litter Incidence | N | 2 | 0 | 0 | 0 |
| % | 8.3 | 0.0 | 0.0 | 0.0 |
Affected fetuses per Litter | MEAN% | 1.2 | 0.0 | 0.0 | 0.0 |
| SD | 5.8 | 0.0 | 0.0 | 0.0 |
TABLE S16-4. SUMMARY DATA OF FETAL SOFT TISSUE VARIATIONS AND OTHER ALTERATIONS: FINDINGS WERE NOT CONSIDERED TO BE ASSOCIATED WITH ADMINISTRATION OF THE TEST ITEM, CONTINUATION
GROUP: | 1 (0 mg/kg) | 2 (36 mg/kg) | 3 (120 mg/kg) | 4 (330 mg/kg) | |
Litters Evaluated | N | 24 | 21 | 24 | 23 |
Fetuses Evaluated | N | 153 | 138 | 149 | 139 |
Males | N | 89 | 67 | 81 | 75 |
Females | N | 64 | 71 | 68 | 64 |
KIDNEY |
|
|
|
|
|
KIDNEY - Malpositioned |
|
|
|
| |
Fetal Incidence | N | 0 | 1 | 1 | 2 |
| % | 0.0 | 0.7 | 0.7 | 1.4 |
Litter Incidence | N | 0 | 1 | 1 | 2 |
| % | 0.0 | 4.8 | 4.2 | 8.7 |
Affected fetuses per Litter | MEAN% | 0.0 | 0.8 | 0.6 | 1.0 |
| SD | 0.0 | 3.6 | 2.9 | 3.4 |
KIDNEY - Altered texture |
|
|
|
| |
Fetal Incidence | N | 0 | 1 | 1 | 0 |
| % | 0.0 | 0.7 | 0.7 | 0.0 |
Litter Incidence | N | 0 | 1 | 1 | 0 |
| % | 0.0 | 4.8 | 4.2 | 0.0 |
Affected fetuses per Litter | MEAN% | 0.0 | 0.6 | 0.5 | 0.0 |
| SD | 0.0 | 2.7 | 2.3 | 0.0 |
KIDNEY - Large |
|
|
|
| |
Fetal Incidence | N | 0 | 1 | 0 | 0 |
| % | 0.0 | 0.7 | 0.0 | 0.0 |
Litter Incidence | N | 0 | 1 | 0 | 0 |
| % | 0.0 | 4.8 | 0.0 | 0.0 |
Affected fetuses per Litter | MEAN% | 0.0 | 0.8 | 0.0 | 0.0 |
| SD | 0.0 | 3.6 | 0.0 | 0.0 |
URINARY BLADDER |
|
|
|
|
|
URINARY BLADDER - Discolored (dark) |
|
|
|
|
|
Fetal Incidence | N | 0 | 2 | 0 | 0 |
| % | 0.0 | 1.4 | 0.0 | 0.0 |
Litter Incidence | N | 0 | 2 | 0 | 0 |
| % | 0.0 | 9.5 | 0.0 | 0.0 |
Affected fetuses per Litter | MEAN% | 0.0 | 1.3 | 0.0 | 0.0 |
| SD | 0.0 | 4.0 | 0.0 | 0.0 |
URINARY BLADDER - Small |
|
|
|
|
|
Fetal Incidence | N | 0 | 1 | 0 | 0 |
| % | 0.0 | 0.7 | 0.0 | 0.0 |
Litter Incidence | N | 0 | 1 | 0 | 0 |
| % | 0.0 | 4.8 | 0.0 | 0.0 |
Affected fetuses per Litter | MEAN% | 0.0 | 0.8 | 0.0 | 0.0 |
| SD | 0.0 | 3.6 | 0.0 | 0.0 |
TABLE S16-4. SUMMARY DATA OF FETAL SOFT TISSUE VARIATIONS AND OTHER ALTERATIONS: FINDINGS WERE NOT CONSIDERED TO BE ASSOCIATED WITH ADMINISTRATION OF THE TEST ITEM, CONTINUATION
GROUP: | 1 (0 mg/kg) | 2 (36 mg/kg) | 3 (120 mg/kg) | 4 (330 mg/kg) | |
Litters Evaluated | N | 24 | 21 | 24 | 23 |
Fetuses Evaluated | N | 153 | 138 | 149 | 139 |
Males | N | 89 | 67 | 81 | 75 |
Females | N | 64 | 71 | 68 | 64 |
TESTIS - Malpositioned |
|
|
|
|
|
Fetal Incidence | N | 5 | 5 | 4 | 6 |
| % | 5.6 | 7.5 | 4.9 | 8.0 |
Litter Incidence | N | 5 | 4 | 4 | 5 |
| % | 20.8 | 19.0 | 16.7 | 21.7 |
Affected fetuses per Litter | MEAN% | 5.3 | 7.9 | 6.3 | 10.4 |
| SD | 10.8 | 18.5 | 15.2 | 24.6 |
VAS DEFERENS - Long |
|
|
|
| |
Fetal Incidence | N | 2 | 1 | 0 | 0 |
| % | 2.2 | 1.5 | 0.0 | 0.0 |
Litter Incidence | N | 2 | 1 | 0 | 0 |
| % | 8.3 | 4.8 | 0.0 | 0.0 |
Affected fetuses per Litter | MEAN% | 2.2 | 1.2 | 0.0 | 0.0 |
| SD | 7.8 | 5.5 | 0.0 | 0.0 |
OVARIES - Small |
|
|
|
| |
Fetal Incidence | N | 0 | 0 | 0 | 1 |
| % | 0.0 | 0.0 | 0.0 | 1.6 |
Litter Incidence | N | 0 | 0 | 0 | 1 |
| % | 0.0 | 0.0 | 0.0 | 4.3 |
Affected fetuses per Litter | MEAN% | 0.0 | 0.0 | 0.0 | 2.2 |
| SD | 0.0 | 0.0 | 0.0 | 10.4 |
UTERUS |
|
|
|
|
|
UTERUS - Discolored (dark) |
|
|
|
| |
Fetal Incidence | N | 0 | 2 | 0 | 0 |
| % | 0.0 | 2.8 | 0.0 | 0.0 |
Litter Incidence | N | 0 | 2 | 0 | 0 |
| % | 0.0 | 9.5 | 0.0 | 0.0 |
Affected fetuses per Litter | MEAN% | 0.0 | 2.8 | 0.0 | 0.0 |
| SD | 0.0 | 8.9 | 0.0 | 0.0 |
UTERINE HORNS - Short |
|
|
|
| |
Fetal Incidence | N | 0 | 1 | 0 | 0 |
| % | 0.0 | 1.4 | 0.0 | 0.0 |
Litter Incidence | N | 0 | 1 | 0 | 0 |
| % | 0.0 | 4.8 | 0.0 | 0.0 |
Affected fetuses per Litter | MEAN% | 0.0 | 1.6 | 0.0 | 0.0 |
| SD | 0.0 | 7.3 | 0.0 | 0.0 |
TOTAL AFFECTED FETUSES |
|
|
|
|
|
Fetal Incidence | N | 45 | 40 | 52 | 46 |
| % | 29.4 | 29.0 | 34.9 | 33.1 |
Litter Incidence | N | 18 | 17 | 18 | 21 |
| % | 75.0 | 81.0 | 75.0 | 91.3 |
Affected fetuses per Litter | MEAN% | 29.9 | 29.5 | 34.4 | 34.5 |
| SD | 29.7 | 24.7 | 29.9 | 31.4 |
TABLE S17-1. SUMMARY DATA OF FETAL SKELETAL MALFORMATIONS
GROUP: | 1 (0 mg/kg) | 2 (36 mg/kg) | 3 (120 mg/kg) | 4 (330 mg/kg) | |
Litters Evaluated | N | 24 | 21 | 24 | 23 |
Fetuses Evaluated | N | 156 | 139 | 153 | 142 |
VERTEBRAE - Absent |
|
|
|
|
|
Fetal Incidence | N | 0 | 0 | 0 | 1 |
| % | 0.0 | 0.0 | 0.0 | 0.7 |
Litter Incidence | N | 0 | 0 | 0 | 1 |
| % | 0.0 | 0.0 | 0.0 | 4.3 |
Affected fetuses per Litter | MEAN% | 0.0 | 0.0 | 0.0 | 0.6 |
| SD | 0.0 | 0.0 | 0.0 | 3.0 |
RIBS - Absent |
|
|
|
|
|
Fetal Incidence | N | 0 | 0 | 0 | 1 |
| % | 0.0 | 0.0 | 0.0 | 0.7 |
Litter Incidence | N | 0 | 0 | 0 | 1 |
| % | 0.0 | 0.0 | 0.0 | 4.3 |
Affected fetuses per Litter | MEAN% | 0.0 | 0.0 | 0.0 | 0.6 |
| SD | 0.0 | 0.0 | 0.0 | 3.0 |
HINDPAW PHALANX - Absent |
|
|
|
|
|
Fetal Incidence | N | 0 | 0 | 0 | 1 |
| % | 0.0 | 0.0 | 0.0 | 0.7 |
Litter Incidence | N | 0 | 0 | 0 | 1 |
| % | 0.0 | 0.0 | 0.0 | 4.3 |
Affected fetuses per Litter | MEAN% | 0.0 | 0.0 | 0.0 | 0.6 |
| SD | 0.0 | 0.0 | 0.0 | 3.0 |
TABLE S17-2. SUMMARY DATA OF FETAL SKELETAL AND CARTILAGE VARIATIONS
GROUP: | 1 (0 mg/kg) | 2 (36 mg/kg) | 3 (120 mg/kg) | 4 (330 mg/kg) | |
Litters Evaluated | N | 24 | 21 | 24 | 23 |
Fetuses Evaluated | N | 156 | 139 | 153 | 142 |
STERNEBRA |
|
|
|
|
|
Incomplete ossification of 2nd to 4th sternebra | |||||
Fetal Incidence | N | 19 | 7 | 11 | 30 |
| % | 12.2 | 5.0 | 7.2 | 21.1 (b) |
Litter Incidence | N | 11 | 11 | 11 | 16 |
| % | 45.8 | 52.4 | 45.8 | 69.6 |
Unossified 6th sternebra |
|
|
|
|
|
Fetal Incidence | N | 12 | 2 | 10 | 23 |
| % | 7.7 | 1.4 | 6.5 | 16.2 (b) |
Litter Incidence | N | 5 | 5 | 5 | 13 |
| % | 20.8 | 23.8 | 20.8 | 56.5 (b) |
Incomplete ossification in 5th sternebra |
|
|
|
| |
Fetal Incidence | N | 19 | 9 | 22 | 18 |
| % | 12.2 | 6.5 | 14.4 | 12.7 |
Litter Incidence | N | 9 | 9 | 9 | 11 |
| % | 37.5 | 42.9 | 37.5 | 47.8 |
Incomplete ossification in 6th sternebra |
|
|
|
| |
Fetal Incidence | N | 33 | 23 | 26 | 42 |
| % | 21.2 | 16.5 | 17.0 | 29.6 |
Litter Incidence | N | 13 | 13 | 13 | 18 |
| % | 54.2 | 61.9 | 54.2 | 78.3 |
TOTAL AFFECTED IN STERNEBRA |
|
|
|
|
|
Fetal Incidence | N | 57 | 28 | 46 | 76 |
| % | 36.5 | 20.1 | 30.1 | 53.5 (a) |
Litter Incidence | N | 17 | 17 | 17 | 20 |
| % | 70.8 | 81.0 | 70.8 | 87.0 |
Affected fetuses per Litter | MEAN% | 34.1 | 20.8 | 29.6 | 57.5 (c) |
| SD | 29.2 | 25.8 | 25.8 | 34.6 |
(a) Significantly different from control group 1 at 0.01 using Fisher Exact test;
(b) Significantly different from control group 1 at 0.05 using Fisher Exact test;
(c) Significantly different from control group 1 at 0.01 using Kruscal-Wallis test
TABLE S17-2. SUMMARY DATA OF FETAL SKELETAL AND CARTILAGE VARIATIONS, CONTINUATION
GROUP: | 1 (0 mg/kg) | 2 (36 mg/kg) | 3 (120 mg/kg) | 4 (330 mg/kg) | |
Litters Evaluated | N | 24 | 21 | 24 | 23 |
Fetuses Evaluated | N | 156 | 139 | 153 | 142 |
RIBS |
|
|
|
|
|
Rib - Supernumerary – 14th | |||||
Fetal Incidence | N | 0 | 0 | 1 | 0 |
| % | 0.0 | 0.0 | 0.7 | 0.0 |
Litter Incidence | N | 0 | 0 | 1 | 0 |
| % | 0.0 | 0.0 | 4.2 | 0.0 |
Rib, Costal cartilage - Not articulated with sternum |
|
|
|
| |
Fetal Incidence | N | 1 | 0 | 1 | 0 |
| % | 0.6 | 0.0 | 0.7 | 0.0 |
Litter Incidence | N | 1 | 0 | 1 | 0 |
| % | 4.2 | 0.0 | 4.2 | 0.0 |
Ribs - Unossified |
|
|
|
| |
Fetal Incidence | N | 0 | 0 | 0 | 1 |
| % | 0.0 | 0.0 | 0.0 | 0.7 |
Litter Incidence | N | 0 | 0 | 0 | 1 |
| % | 0.0 | 0.0 | 0.0 | 4.3 |
TOTAL AFFECTED IN RIBS |
|
|
|
|
|
Fetal Incidence | N | 1 | 0 | 2 | 1 |
| % | 0.6 | 0.0 | 1.3 | 0.7 |
Litter Incidence | N | 1 | 0 | 2 | 1 |
| % | 4.2 | 0.0 | 8.3 | 4.3 |
Affected fetuses per Litter | MEAN% | 4.2 | 0.0 | 1.3 | 0.6 |
| SD | 0.7 | 0.0 | 4.6 | 3.0 |
METACARPAL |
|
|
|
|
|
Unossified 5th Metacarpal | |||||
Fetal Incidence | N | 34 | 19 | 25 | 66 |
| % | 21.8 | 13.7 | 16.3 | 46.5 (a) |
Litter Incidence | N | 11 | 11 | 11 | 21 |
| % | 45.8 | 52.4 | 45.8 | 91.3 (b) |
Incomplete ossification of 5th Metacarpal |
|
|
|
| |
Fetal Incidence | N | 7 | 4 | 7 | 16 |
| % | 4.5 | 2.9 | 4.6 | 11.3 (c) |
Litter Incidence | N | 6 | 6 | 6 | 9 |
| % | 25.0 | 28.6 | 25.0 | 39.1 |
TOTAL AFFECTED IN METACARPAL |
|
|
|
|
|
Fetal Incidence | N | 41 | 23 | 32 | 83 |
| % | 26.3 | 16.5 | 20.9 | 58.5 (a) |
Litter Incidence | N | 13 | 13 | 13 | 21 |
| % | 54.2 | 61.9 | 54.2 | 91.3 (b) |
Affected fetuses per Litter | MEAN% | 23.2 | 15.9 | 19.1 | 60.7 (d) |
| SD | 29.2 | 17.5 | 27.3 | 34.2 |
(a) Significantly different from control group 1 at 0.001 using Fisher Exact test;
(b) Significantly different from control group 1 at 0.01 using Fisher Exact test;
(c) Significantly different from control group 1 at 0.05 using Fisher Exact test;
(d) Significantly different from control group 1 at 0.01 using Kruscal-Wallis test
TABLE S17-2. SUMMARY DATA OF FETAL SKELETAL AND CARTILAGE VARIATIONS, CONTINUATION
GROUP: | 1 (0 mg/kg) | 2 (36 mg/kg) | 3 (120 mg/kg) | 4 (330 mg/kg) | |
Litters Evaluated | N | 24 | 21 | 24 | 23 |
Fetuses Evaluated | N | 156 | 139 | 153 | 142 |
FIBULA |
|
|
|
|
|
Bent | |||||
Fetal Incidence | N | 0 | 0 | 0 | 1 |
| % | 0.0 | 0.0 | 0.0 | 0.7 |
Litter Incidence | N | 0 | 0 | 0 | 1 |
| % | 0.0 | 0.0 | 0.0 | 4.3 |
Affected fetuses per Litter | MEAN% | 0.0 | 0.0 | 0.0 | 0.7 |
| SD | 0.0 | 0.0 | 0.0 | 3.5 |
METATARSAL |
|
|
|
|
|
Incomplete ossification of 5th Metatarsal |
|
|
|
| |
Fetal Incidence | N | 2 | 0 | 0 | 1 |
| % | 1.3 | 0.0 | 0.0 | 0.7 |
Litter Incidence | N | 1 | 0 | 0 | 1 |
| % | 4.2 | 0.0 | 0.0 | 4.3 |
Affected fetuses per Litter | MEAN% | 1.2 | 0.0 | 0.0 | 0.5 |
| SD | 5.8 | 0.0 | 0.0 | 2.3 |
TOTAL AFFECTED FETUSES |
|
|
|
|
|
Fetal Incidence | N | 70 | 36 | 62 | 100 (a) |
| % | 44.9 | 25.9 | 40.5 | 70.4 |
Litter Incidence | N | 17 | 17 | 17 | 21 |
| % | 70.8 | 81.0 | 70.8 | 91.3 |
Affected fetuses per Litter | MEAN% | 41.1 | 26.3 | 39.3 | 72.6 (b) |
| SD | 37.0 | 25.8 | 30.5 | 33.5 |
(a) Significantly different from control group 1 at 0.001 using Fisher exact test;
(b) Significantly different from control group 1 at 0.01 using Kruscal-Wallis test
Historical Control Data Summary on Reproductive Toxicity Studies
Test Facility:
Biological Testing Laboratory (BTL)
Branch of Shemyakin and Ovchinnikov Institute of Bioorganic Chemistry
Russian Academy of Sciences (BIBC RAS)
Prospect Nauki 6, Pushchino
Moscow Region 142290
Russia
HISTORICAL CONTROL SUMMARY DATA OF FORMER IMPLANTATION SITES, NUMBER OF CORPORA LUTEA, IMPLANTATION LOSS INDICES, NUMBER OF FETUSES IN FEMALES EUTHANIZED ON GESTATION DAYS 19-20
Species / Strain: Rat / Sprague-Dawley | ||||||
Number of studies: 4 (a) | Range of Study Dates: | August 2012 - February 2014 | ||||
| MEAN | S.D. | N | Min / Max Value | ||
CONTROL – VEHICLE FEMALES |
|
|
|
|
|
|
Number of corpora lutea, N per female | 14.4 | 4.0 | 77 | 1.0 | / | 23.0 |
Number of implantation sites, N per female | 13.9 | 3.2 | 38 | 7.0 | / | 21.0 |
Pre-implantation loss, N per female | 1.9 | 3.4 | 38 | 0.0 | / | 13.0 |
Pre-implantation loss (% per female) | 10.9 | 18.5 | 38 | 0.0 | / | 61.9 |
Live fetuses, N per female | 12.7 | 4.0 | 77 | 1.0 | / | 21.0 |
Dead fetuses, N per female | 0.0 | 0.0 | 77 | 0.0 | / | 0.0 |
Post-implantation loss, N per female | 0.8 | 1.1 | 77 | 0.0 | / | 5.0 |
Post-implantation loss (% per female) | 5.8 | 8.1 | 77 | 0.0 | / | 35.7 |
(a) Studies of prenatal toxicity of some clinical drugs carried out in accordance with the methodological guidelines of the Ministry of Health of the Russian Federation
HISTORICAL CONTROL SUMMARY DATA OF FETAL BODY WEIGHT ON PRENATAL DAY 20
Species / Strain: Rat / Sprague-Dawley | ||||||
Number of studies: 1 | Range of Study Dates: | January - February 2014 | ||||
| MEAN | S.D. | N | Min / Max Value | ||
Mean body weight for male and female fetuses, g | 3.91 | 0.39 | 258 | 2.36 | / | 4.79 |
Mean fetal body weight per litter, g | 3.87 | 0.35 | 20 | 2.75 | / | 4.43 |
Note: Separate body weight data for each sex of fetuses on GD20 are not available for historical studies as well as data on AGD and % males in prenatal toxicity studies (before 2019). As historical control data of % males in the litter, the data of studies in accordance with the OECD 422 can be used (see table below).
SUMMARY OF HISTORICAL CONTROL DATA ON NUMBER OF PUPS PER LITTER, SEX, AND % MALES
Species / Strain: Rat / Sprague-Dawley Number of Studies: 5 (b) | |||||||
Range of Study Dates: November 2017 – January 2019 | |||||||
| N | MEAN | SD | MEAN +/- 2 SD | Min | Max | |
Number of litters | 53 |
|
|
|
|
|
|
Number of pups, N | 651 |
|
|
|
|
|
|
females, N | 321 |
|
|
|
|
|
|
males, N | 329 |
|
|
|
|
|
|
% males, total | 50.5 |
|
|
|
|
|
|
Number of pups per litter |
| 12.3 | 2.4 | 7.5 | 17.1 | 6.0 | 19.0 |
females per litter, N |
| 6.2 | 2.0 | 2.2 | 10.2 | 2.0 | 11.0 |
males per Litter, N |
| 6.0 | 2.3 | 1.4 | 11.1 | 2.0 | 11.0 |
(b) Screening studies of repeated dose oral toxicity with the reproduction/developmental toxicity (OECD TG 422)
HISTORICAL CONTROL SUMMARY DATA OF FETAL SKELETAL AND VISCERAL MALFORMATIONS ON GESTATION DAY 19
Species / Strain: Rat / Sprague-Dawley | |
Number of studies: 3 | Range of Study Dates: August 2012 - February 2014 |
SKELETAL MALFORMATIONS |
|
Litters Evaluated, N | 54 |
Fetuses Evaluated, N | 461 |
Fetal incidence, N | 0 |
Fetal incidence, % | 0.0 |
Litter incidence, N | 0 |
Litter incidence, % | 0.0 |
VISCERAL MALFORMATIONS |
|
Litters Evaluated, N | 57 |
Fetuses Evaluated, N | 260 |
Fetal incidence, N | 0 |
Fetal incidence, % | 0.0 |
Litter incidence, N | 0 |
Litter incidence, % | 0.0 |
Note: Historical control data on skeletal, cartilage, and visceral variations for fetuses on gestation day 20 are not available before December 2019.
Prepared by Oksana Khokhlova,
Ph.D., senior scientist of BTL BIBC RAS, 04.05.2020
Applicant's summary and conclusion
- Conclusions:
- Under the conditions of this study, the no-observed-adverse-effect-level (NOAEL) for maternal
and developmental toxicity (post-implantation loss) of 1,2,3-Benzotriazole was considered to be 36 mg/kg bw/day.
The no-observed-adverse-effect-level (NOAEL) for embryo-fetal developmental toxicity of 1,2,3-Benzotriazole was considered to be 120 mg/kg bw/day - Executive summary:
Objective
The objective of this prenatal developmental toxicity study was to evaluate the potential effects of the test
item, 1,2,3-Benzotriazole (CAS No. 95-14-7), on pregnancy and on embryo-fetal development in rats
following daily oral (gavage) administration at doses 36, 120 and 330 mg/kg body weight/day from
implantation to the day prior to scheduled caesarean section (day 5 to day 19 post-mating inclusive).
Design
Results from the separate dose-range-finding study as well as published toxicity data of 1,2,3-Benzotriazole
and data from a structurally closely related substance (Methyl-1H-benzotriazole, CAS No. 29385-43-1) were
considered for dose selection.
The test item, 1,2,3-Benzotriazole, in the vehicle (Kollisolv® PEG E 400) was administered by gavage once
daily to Sprague-Dawley female rats from day 5 to day 19 post-mating (inclusive). Three groups received
the test item at dose-levels of 36, 120 or 330 mg/kg bw/day. A concurrent vehicle control group received the
vehicle (Kollisolv® PEG E 400) on a comparable regiment and in the same volume of 3 mL/kg bw. Each
group consists of 24-26 females with confirmed mating.
All females were observed twice daily for mortality and morbidity and for signs of toxicity following dose
administration. Body weights and food consumption are recorded at three-day intervals. On day 20 post-
mating, the dams were sacrificed and subjected to a macroscopic examination and enumeration of corpora
lutea. The weight of the thyroid gland, histopathological assessment of the thyroid gland, and assay of
serum concentration of thyroxin (T4), triiodothyronine (T3), and thyroid stimulating hormone (TSH) were
done in dams to observe pathological changes in thyroid function. Gravid uteri were weighed, and uteri
content are examined to record implantation sites, early and late resorptions, dead, and live fetuses. The
fetuses were weighed, sexed with measurement of anogenital distance (AGD), and submitted to external
examination. Approximately half of the fetuses from each litter were subjected to a detailed examination of
soft tissue by serial sectioning after fixation in Bouin’s solution while the other half underwent detailed
skeletal examination following staining of bone with alizarin red and cartilage with alcian blue.
The fetal findings were described according to the harmonized terminology of the International Federation of
Teratology Societies (IFTS) and classified as malformations or variations. Fetal incidence, litter incidence,
and affected fetuses per litter were calculated for external, visceral, and skeletal alterations. The
reproductive tract was examined with particular attention, and external sex was compared with internal
(gonadal) sex in all fetuses. In addition, male fetuses were examined for undescended testes.
Results
There was no morbidity and mortality of females caused by the test item administration. The test item
related clinical findings were observed in the 330 mg/kg bw/day dose group after dosing and were as
follows: hypokinesia, staggering gait or flatness as a more severe behavior disorder, excessive vocalization,
chromodacryorrhea, ptyalism, nasal discharge. Clinical observations were episodic with the recovery of
animals within approximately 1.5 – 3 hours after dosing. The higher frequency of clinical signs was noted
after first dosing (gestation day 5), as well as at the end of the administration period (gestation days 14, 15,
17, and 19). Over the entire period of the test item administration, the total number of females with clinical
findings in the 330 mg/kg bw/day dose group was 14 out of 26 examined (p < 0.001, Fisher Exact test). The
body weight of pregnant females administered with the dose of 330 mg/kg bw/day was slightly decreased
compared to the control vehicle group at the gestation day 20 (by 5.0%, p < 0.05), and the body weight gain
was statistically reduced (p < 0.01) the entire period of administration compared with the control group as
well as lower doses. The reduced body weight gain of pregnant females in the 330 mg/kg bw/day dose
group was associated with a smaller weight of the pregnant uterus (by 16 % compared to the control group,
p < 0.05). The final maternal body weight without a gravid uterus did not statistically differ from the body
weight of control females. Mean food consumption in the 36, 120 and 330 mg/kg bw/day group was similar
to that in the vehicle control group during all study days.
During necropsy, there were no gross findings related to the test item administration. The mean number of
corpora lutea and pre-implantation loss did not statistically differ in the test item treated groups compared to
the control vehicle group. The mean number of implantation sites was approximately the same among
groups.
The test item did not affect the observed thyroid function of pregnant females. The absolute and relative
thyroid weight was not significantly changed in all dose test item treated group. Test item related C-cell
hyperplasia was observed in 3 of 24 females from 120 mg/kg bw/day dose group, and in 4 of 23 females
from 330 mg/kg bw/day groups (p < 0.05, Fisher Exact test). This histological alteration was of minimum
grade and can be associated with the calcitonin exchange (as speculation). Although there is no data on the
serum level of calcitonin and calcium in pregnant females treated with benzotriazole, C-cell hyperplasia may
be considered potentially adverse. The level of thyroid hormones T3, T4, and TSH in the serum of pregnant
females was not significantly changed in the test item treated groups.
The relative post-implantation loss was increased in the 120 and 330 mg/kg bw/day dose groups compared
to the control vehicle group (p < 0.01 and p < 0.05, respectively). The increase of post-implantation loss in
these groups was associated with the increase in the absolute and percentage values of early resorptions.
Also, the total number of females with post-implantation loss was increased (non-significantly) in the 120
and 330 mg/kg bw/day dose groups. The mean number of fetuses per female was slightly decreased in the
330 mg/kg bw/day dose group (by 6.2 % compared to the control group), but this change was not
significant.
The body weight of male and female fetuses, as well as mean fetuses weight of litter, was significantly
decreased in the 330 mg/kg bw/day dose group (respectively, by 11.2 %, 11.8 %, and 11.5 %). The
absolute and normalized anogenital distance was not changed in male fetuses; however, for female fetuses,
the normalized anogenital distance was statistically increased in the 330 mg/kg bw/day dose group. The
fetal sex ratio in all dose treated groups was not significantly changed compared to the control vehicle
group.
In the 36 mg/kg bw/day dose group, there were no fetuses with external observations, soft tissue, and
skeletal and cartilage alterations recognized as malformations; there were no variations or other alterations
which are considered as test item related.
In the 120 mg/kg bw/day dose group, three fetuses from one litter were with inward rotated hindlimbs during
an external examination. No skeletal and visceral malformations were observed for these fetuses; however,
the altered ossifications were noted for two of them. Besides, these fetuses had a domed head as an
external observation with unknown importance, and the dilated ventricles of the brain were noted for one of
them. The fetal and litter incidence of dilated brain ventricles (fourth, third, lateral and ventricle) was
statistically increased in the 120 mg/kg bw/day dose group compared to the control group (p < 0.01 for
ventricle) as well as the incidence of the dilated renal pelvis (p < 0.01). These findings were not dose-
dependent. In the 330 mg/kg bw/day dose group, the dilation of the fourth brain ventricle was found in 4
fetuses from 2 litters, and the dilation of the renal pelvis was found in 1 fetus, which was not significantly
higher compared to the control group. So, in the 120 mg/kg bw/day dose group, the dilated brain ventricles
and dilated renal pelvis as soft tissue alterations of unknown importance are considered to be with unclear
relation to the test item administrations. In 120 mg/kg bw/day dose group, there was no significant increase
in the fetal and litter incidence of skeletal and cartilage observations.
In the 330 mg/kg bw/day dose group, one female fetus had following external malformations: inward rotated
hindlimbs, absent of some digits on the left hindlimb, thread-like tail, and absent of anus confirmed during
evisceration. This fetus also had a large abdomen, probably as a result of the absence of the anus; no other
malformations of soft tissues were found during evisceration. The external malformations in the fetus were
associated with the skeletal malformations: the absence of vertebrae after the thoracic T4, and the presence
of only seven ribs on the right and left, of which the 5th, 6th, and 7th pairs were unossified, and unilateral
absence of hindpaw phalanges. Despite the uniqueness of this finding, it considered being test item-related.
In this group, the increase in the incidence of altered fetal ossification was observed. The statistical
significant increase in incidence compared to the control vehicle group was noted for incomplete ossification
of 2nd - 4th sternebra (fetal incidence, p < 0.05), unossification of 6th sternebra (fetal and litter incidence, p
< 0.05), unossification in 5th metacarpal (fetal and litter incidence, p < 0.001 and p < 0.01) or its incomplete
ossification (fetal incidence, p < 0.05). The total affected fetuses with alteration in ossification was
statistically increased for sternebra (fetal incidence, and mean of fetus per litter, p < 0.01), for metacarpal
(fetal and litter incidence, and mean of fetus per litter, p < 0.01), and for total variations (fetal incidence, p <
0.001, and mean of fetus per litter, p < 0.01). Moreover, in the 330 mg/kg bw/day dose group, the statistical
increase in the incidence of soft tissue variations was observed for the liver (discoloration - pale, spotted),
kidney (discolored due to the hemorrhage), and uterus (thin uterine horns). The percentage increase was
observed for the fetal incidence (liver and kidney), as well as for the litter incidence (kidney, uterus, and liver
(non-significant)). The slight non-statistical dose-dependence was noted for these findings, so, they are
considered as test item related. It should be noted that thin uterine horns are regarded as of unknown
importance and may be due to the small fetuses in the high dose group, recorded during an external
examination.
The fetal and litter incidence of testis malposition was the same in the test item treated and control groups.
In most fetuses, this observation was expressed as a unilateral undescended testis at half the distance from
the kidney.
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