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EC number: 260-694-8 | CAS number: 57357-85-4
- Life Cycle description
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- Endpoint summary
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- 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
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- Toxicological Summary
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- Acute Toxicity
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- Toxicity to reproduction
- Specific investigations
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- Additional toxicological data
Endpoint summary
Administrative data
Key value for chemical safety assessment
Effects on fertility
Description of key information
In a reproductive screening test according to OECD Guideline 422, a NOAEL of 75 mg/kg bw/d (highest tested concentration) based on reproductive performance and fertility was determined (BASF, 2018). The NOAEL for developmental toxicity in the F1 offspring was 25 mg/kg bw/d due to a delay in body weight development of F1 male and female pups at 75 mg/kg bw/d.
Link to relevant study records
- Endpoint:
- screening for reproductive / developmental toxicity
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Study period:
- 2016-08-12 to Nov. 2017
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- guideline study
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 422 (Combined Repeated Dose Toxicity Study with the Reproduction / Developmental Toxicity Screening Test)
- Version / remarks:
- 2015-07-28
- Deviations:
- no
- Qualifier:
- according to guideline
- Guideline:
- other: OPPTS 870.3650: Combined Repeated Dose Toxicity Study with the Reproduction/Developmental Toxicity Screening Test (
- Version / remarks:
- 2000-07
- Deviations:
- no
- GLP compliance:
- yes (incl. QA statement)
- Limit test:
- no
- Justification for study design:
- SPECIFICATION OF STUDY DESIGN
- Premating exposure duration for parental (P0) animals: 14 days
- Basis for dose level selection: Request of the sponsor, based on a dose range finding study
- Route of administration: Oral gavage - Specific details on test material used for the study:
- SOURCE OF TEST MATERIAL
- Batch No. of test material: WE 20PA15
- Expiration date of the batch: 2017-11-26
PURITY
Sum or all relevant peaks: 99.6%
CONTENT:
Main component nd diastereomers: > 98 g/100g
STABILITY AND STORAGE CONDITIONS OF TEST MATERIAL
- Storage condition of test material: Room temperature
OTHER SPECIFICS:
- Liquid / colorless, clear - Species:
- rat
- Strain:
- Wistar
- Remarks:
- Crl:WI(Han)
- Details on species / strain selection:
- The test guidelines require the rat to be used as the animal species. This rat strain was selected since extensive historical control data are available for Wistar rats.
- Sex:
- male/female
- Details on test animals or test system and environmental conditions:
- TEST ANIMALS
- Source: Charles River Laboratories, Research Models and Services, Germany GmbH
- Females nulliparous and non-pregnant: yes
- Age at study initiation:
(P) males: 11 - 12 weeks; females: 10 weeks
- Weight at study initiation:
(P) Males: 357.7 - 414.5 g; Females: 193.6 - 226.3 g;
- Housing: During pre-treatment of the study period, the rats were housed together (up to 5 animals per sex and cage) in Polysulfonate cages Typ 2000P (H-Temp). During the study period, the rats were housed individually in Polycarbonate cages type III with the following exceptions:
- During overnight matings, male and female mating partners were housed together in Polycarbonate cages type III.
- Diet: Kliba maintenance diet mouse/rat “GLP” meal, supplied by Provimi Kliba SA, Kaiseraugst, Switzerland, ad libitum
- Water: Drinking water, ad libitum
- Acclimation period: at least 20 days
ENVIRONMENTAL CONDITIONS
- Temperature (°C): 20 - 24
- Humidity (%): 30 - 70
- Air changes (per hr): 15
- Photoperiod (hrs dark / hrs light): 12/12 - Route of administration:
- oral: gavage
- Vehicle:
- CMC (carboxymethyl cellulose)
- Details on exposure:
- PREPARATION OF DOSING SOLUTIONS:
For the test substance preparation, the specific amount of test substance was weighed, topped up with 0.5 % Sodium carboxymethyl cellulose with 5 mg/100 mL Tween 80 suspension in drinking water in a calibrated beaker and intensely mixed with a magnetic stirrer.
VEHICLE
- Justification for use and choice of vehicle: Homogeneous distribution of the test substance in the vehicle
- Concentration in vehicle: 0.5 %
- Amount of vehicle: 10 mL/kg bw/day - Details on mating procedure:
- - M/F ratio per cage: 1/1
- Length of cohabitation: overnight, maximum 2 weeks
- Proof of pregnancy: sperm in vaginal smear referred to as day 0 of pregnancy (GD 0)
- After successful mating each pregnant female was caged: Pregnant animals and their litters were housed together until PND 13 in polycarbonate cages type III.
- Any other deviations from standard protocol: No - Analytical verification of doses or concentrations:
- yes
- Details on analytical verification of doses or concentrations:
- Test substance concentrations were determined via GC (Shimadzu 2010 plus, FID, Dionex Chromeleon Software (dionex), or equivalent system). Based on the analytical results it is concluded that the test substance is stable in 0.5 % carboxymethyl cellulose in drinking water + Tween 80 (5 mg/100 mL) over a period of 7 days at a target concentration of 50 mg/100 mL at ambient temperature and over a period of 4 days at a target concentration of 1000 mg/100 mL also at ambient temperature. All determined concentrations were in the range of 90 % - 110 % of the nominal concentration.
- Duration of treatment / exposure:
- The duration of treatment covered a 2-week pre-mating and a mating period in both sexes, one day post-mating in males, and the entire gestation period as well as up to 22 days of the lactation period in females.
- Frequency of treatment:
- Daily
- Dose / conc.:
- 5 mg/kg bw/day
- Dose / conc.:
- 25 mg/kg bw/day
- Dose / conc.:
- 75 mg/kg bw/day
- No. of animals per sex per dose:
- 10
- Control animals:
- yes, concurrent vehicle
- Details on study design:
- - Dose selection rationale: Sponsors request
- Rationale for animal assignment: The assignment of the animals to the different test groups was carried out using a randomization program, according to their weight one day (male and female animals) before the beginning of the administration period (day -1). - Parental animals: Observations and examinations:
- CAGE SIDE OBSERVATIONS: Yes
- Time schedule: Daily
- Cage side observations were included.
DETAILED CLINICAL OBSERVATIONS: Yes
- Time schedule: Detailed clinical observations (DCO) were performed in all animals once prior to the first administration (day 0) and at weekly intervals during the administration period. The examinations started in the morning.
BODY WEIGHT: Yes
- Time schedule for examinations: The body weight of the male and female parental animals was determined once a week at the same time of the day (in the morning) until sacrifice.
FOOD CONSUMPTION AND COMPOUND INTAKE:
- Food consumption was determined once a week for male and female parental animals. Food consumption was not determined after the 2nd premating week (male parental animals) and during the mating period (male and female F0 animals). Food consumption of the F0 females with evidence of sperm was determined on gestation days (GD) 0-7, 7-14, and 14-20. Food consumption of F0 females which gave birth to a litter was determined on PND 1-4, 4-7, 7-10 and 10-13. Food consumption was not determined in females without positive evidence of sperm during the mating and the gestation period and in females without litter during the lactation period.
OTHER:
A functional observational battery (FOB) was performed in the first five male and the first 5 female animals with litter per group (in order of delivery) at the end of the administration period starting at about 10.00 h. The FOB started in a randomized sequence with passive observations without disturbing the animals, followed by removal from the home cage, open field observations in a standard arena and sensorimotor tests as well as reflex tests. The findings were ranked according to the degree of severity, if applicable. The observations were performed at random.
The measurement of motor activity (MA) was measured at the end of the administration period in the first 5 surviving parental males and the first 5 surviving females with litter (in order of delivery) per group. Motor activity (MA) was measured from 14:00 h onwards on the same day as the FOB was performed. The examinations were performed using the TSE Labmaster System supplied by TSE Systems GmbH, Bad Homburg, Germany. For this purpose, the animals were placed in new clean polycarbonate cages with a small amount of bedding for the duration of the measurement.
Hematology: Leukocyte count (WBC), Erythrocyte count (RBC), Hemoglobin (HGB), Hematocrit (HCT), Mean corpuscular volume (MCV), Mean corpuscular hemoglobin (MCH), Mean corpuscular hemoglobin concentration (MCHC), Platelet count (PLT), Differential blood count, Reticulocytes (RET), Prothrombin time (Hepato Quick’s test) (HQT), blood smears
Clinical chemistry: Alanine aminotransferase (ALT), Aspartate aminotransferase (AST), Alkaline phosphatase (ALP), gamma-Glutamyltransferase (GGT), Sodium, Potassium, Chloride, Inorganic phosphate, Calcium, Urea, Creatinine, Total bilirubin, Total Protein, Albumin, Globulins, Triglycerides, Cholesterol, Bile acids,
Thyroid hormones: Total thyroxine (T4) - Oestrous cyclicity (parental animals):
- For all females of the pool, estrous cycle normality was evaluated before the beginning of the administration period. In all parental females in the premating phase, estrous cycle length and normality was evaluated by preparing vaginal smears during a minimum of 2 weeks prior to premating, mating and throughout cohabitation until there is evidence of sperm in the vaginal smear. Additionally, on the day of scheduled sacrifice, the estrous status was also determined in all female F0 rats.
- Sperm parameters (parental animals):
- Parameters examined in P male parental generation:
Weight: testis, epididymis, bulbourethral gland (cowper’s gland), glans penis, M. levator ani together with musc. bulbocavernosus, prostate, seminal vesicles with coagulating glands - Litter observations:
- STANDARDISATION OF LITTERS
- Performed on day 4 postpartum: yes
- If yes, maximum of 8 pups/litter (4 /sex/litter as nearly as possible); excess pups were sacrificed and blood samples were taken for possible determination of thyroid hormone concentrations. After sacrifice, these pups were examined externally, eviscerated and their organs were assessed macroscopically
PARAMETERS EXAMINED
number and sex of pups, stillbirths, live births, postnatal mortality, presence of gross anomalies, weight gain, physical or behavioural abnormalities, anogenital distance (AGD), anogenital index (ADI), presence of nipples/areolae in male pups, other: determination of thyroid hormone concentrations
GROSS EXAMINATION OF DEAD/SACRIFICED PUPS:
yes, for external and internal abnormalities; possible cause of death was not determined for pups born or found dead.
ASSESSMENT OF DEVELOPMENTAL NEUROTOXICITY: No
ASSESSMENT OF DEVELOPMENTAL IMMUNOTOXICITY: No - Postmortem examinations (parental animals):
- SACRIFICE
- Male animals: All surviving animals were sacrificed on study day 29.
- Maternal animals: All surviving animals were sacrificed after weaning of the pups.
GROSS NECROPSY
- Gross pathological assessment of all animals, with special attention being given to the reproductive organs.
HISTOPATHOLOGY
The tissues indicated in Table 1 were prepared for microscopic examination
ORGAN WEIGHTS
The following weights were determined in all animals sacrificed on schedule:
1. Anesthetized animals
2. Bulbourethral gland (Cowper’s gland)
3. Epididymides
4. Glans penis
5. M. levator ani together with musc. bulbocavernosus (males only)
6. Prostate
7. Seminal vesicles with coagulating glands
8. Testes
9. Thyroid glands (fixed)
The following weights were determined in 5 animals per sex/test group sacrificed on schedule
(females with litters only, same animals as used for clinical pathological examinations):
1. Adrenal glands
2. Brain
3. Heart
4. Kidneys
5. Liver
6. Spleen
7. Thymus - Postmortem examinations (offspring):
- SACRIFICE
- On PND 4, as a result of standardization, the surplus pups were sacrificed.
- These animals were subjected to postmortem examinations (macroscopic and/or microscopic examination) as follows:
Blood was sampled for determination of thyroid hormone concentrations. After sacrifice, the pups were examined externally and eviscerated, and the organs were assessed macroscopically.
- On PND 13, one selected male and one female pup per litter was sacrificed.
- Blood was sampled for determination of thyroid hormone concentrations. Thyroid glands/parathyroid glands were fixed in neutral buffered 4 % formaldehyde solution and were transferred to the pathology laboratory for further processing. The remaining pups were sacrificed under isoflurane anesthesia with CO2. After sacrifice, these pups were examined externally, eviscerated and their organs were assessed macroscopically.
GROSS NECROPSY
- All stillborn pups and all pups that died before weaning were examined externally, eviscerated and their organs were assessed macroscopically. All pups without notable findings or abnormalities were discarded after their macroscopic evaluation. Animals with notable findings or abnormalities were evaluated on a case-by-case basis, depending on the type of finding noted.
- Statistics:
- DUNETT-test (two-sided): Food consumption (parental animals), body weight and body weight change (parental animals and pups; for the pup weights, the litter means were used), gestation days, anogenital distance, anogenital index
FISHER`S EXACT test: Male and female mating indices, male and female fertility indices, females mated, females delivering, gestation index (females with liveborn pups), females with stillborn pups, females with all stillborn pups
WILCOXON test (one-sided+) with BONFERRONI-HOLM adjustment: Mating days until day 0 pc, %-postimplantation loss, pups stillborn, %-perinatal loss, nipple developmentWILCOXON test (one-sided-) with BONFERRONI-HOLM adjustment: Implantation sites, pups delivered, pups liveborn, live pups day x, viability index, survival index
WILCOXON test (two-sided): %-live male day x, %-live female day x
KRUSKAL-WALLIS test (two-sided): Number of cycles and cycle length, rearing, grip strength of forelimbs and hindlimbs, landing foot-splay test, motor activity - Reproductive indices:
- Male mating index, male fertility index
Female mating index, gestation index - Offspring viability indices:
- live birth index, viability index
- Clinical signs:
- effects observed, treatment-related
- Description (incidence and severity):
- Up to four mid-dose (25 mg/kg bw/d) and all high-dose (75 mg/kg bw/d) male animals showed slight to severe salivation after treatment during several parts of the premating, mating and post-mating periods.
Up to eight high-dose female animals showed moderate salivation after treatment during premating and mating periods, while during gestation and lactation periods a maximum of five mid-dose females and all high-dose females (grade: slight to severe) showed this finding after treatment.
This transient salivation for a few minutes immediately after treatment was likely to be induced by the unpleasant taste of the test substance or by local irritation of the upper digestive tract.
It is not considered to be a sign of systemic toxicity. No other clinical signs or changes of general behavior, which may be attributed to the test substance, were detected in any of the male and female F0 parental animals in any of the groups during the entire study period. - Mortality:
- no mortality observed
- Description (incidence):
- There were no test substance-related or spontaneous mortalities in any of the groups.
- Body weight and weight changes:
- effects observed, treatment-related
- Description (incidence and severity):
- The mean body weight and body weight change of the mid- and low-dose F0 females and males (25 or 5 mg/kg bw/d) were comparable to the concurrent control group during the entire study period. The body weight change of the high-dose male animals (75 mg/kg bw/d) was statistically significantly decreased during premating days 0-7 (-85 % below control) and, consequently, if calculated for the entire premating period (days 0-13; -49 %). During mating, the body weight change of these animals was slightly reduced without attaining statistical significance (-24 %). This was assessed as treatment-related and adverse. High dose female animlas showed mean body weight (change) values comparable to controls during premating, mating and gestation. During lactation (PND 0-4), females of test group 3 showed a body weight loss and a decrease of body weight change (-5.8 g) without statistical significance. They recovered and gained weight from PND 4 onwards. Although body weight was only affected in one study period during lactation, the significant body weight loss was assessed as treatment-related and adverse.
- Food consumption and compound intake (if feeding study):
- effects observed, treatment-related
- Description (incidence and severity):
- Food consumption of the high-dose F0 males (75 mg/kg bw/d) was statistically significantly below the concurrent control values during premating days 0-7 (around -10 %) and, consequently, if calculated for the entire premating period (days 0-13; around -8 %). This was assessed as treatment-related and adverse. Food consumption of the high-dose F0 females was also statistically significantly reduced during premating days 0-7 (around -8 % below control) and PND 4-7 (around -11 %). This was assessed as treatment-related and adverse. During gestation period, food consumption of the females in test group 3 was comparable to the concurrent control group. The mid- and low-dose F0 parental animals (25 and 5 mg/kg bw/d) did not show any test substance-related changes in food consumption during the entire treatment period.
- Food efficiency:
- not examined
- Water consumption and compound intake (if drinking water study):
- not examined
- Ophthalmological findings:
- not examined
- Haematological findings:
- effects observed, non-treatment-related
- Description (incidence and severity):
- No treatment-related changes among hematological parameters were observed. In males of test group 3 (75 mg/kg bw/d) hematocrit values were significantly lower compared to controls. However, the mean was within the historical control range (males, hematocrit 0.408-0.450 L/L). Therefore, this change was regarded as incidental and not treatment-related.
- Clinical biochemistry findings:
- effects observed, treatment-related
- Description (incidence and severity):
- No treatment-related, adverse changes among clinical chemistry parameters were observed. In males of test group 3 (75 mg/kg bw/d) urea, triglyceride and inorganic phosphate levels were significantly increased. Urea and inorganic phosphate levels were within, triglyceride levels marginally above the historical control range (males, urea 3.93-7.15 mmol/L, inorganic phosphate 1.45-1.98 mmol/L, triglycerides 0.40-1.06 mmol/L). However, higher triglyceride values were the only changed parameter values among these individuals and therefore, this alteration was regarded as treatment-related, but not adverse (ECETOC Technical Report No.85, 2002).
In females of test group 3 (75 mg/kg bw/d) total protein and globulin values were significantly decreased. Both mentioned protein means were slightly below whereas the albumin mean was within the historical control range (females, total protein 58.64-62.26 g/L, globulins 23.40-27.60 g/L; albumin 32.97-36.87 g/L). Total proteins consist of albumin and globulin fractions. Therefore, the decreased globulin levels resulted in decreased total protein levels when albumin values were not changed. The changed globulin levels were the only changed clinical pathology parameter in females of test group 3. Therefore, this alteration was regarded as treatment-related, but not adverse (ECETOC Technical Report No.85, 2002). - Urinalysis findings:
- not examined
- Behaviour (functional findings):
- no effects observed
- Description (incidence and severity):
- No test substance-related or spontaneous findings were observed in male and female animals of all test groups during the home cage observation.
The open field observations did not reveal any test substance-related findings in male and female animals of all test groups.
No statistically significant changes on motor activity data (summation of all intervals) was observed in all male and female animals of all dose groups in comparison to the concurrent control group. - Immunological findings:
- not examined
- Organ weight findings including organ / body weight ratios:
- effects observed, treatment-related
- Description (incidence and severity):
There were no test substance-related findings in male and female animals of all test groups in the sensorimotor tests.- Histopathological findings: non-neoplastic:
- effects observed, treatment-related
- Description (incidence and severity):
- A minimal to slight centrilobular vacuolation of macrovesicular type in 5 out of 10 males was positive in the Oil-Red-O stain, which was consistent with a centrilobular fatty change. Furthermore, 3 out of 10 males showed a minimal centrilobular hypertrophy. These findings were regarded as treatment-related but not adverse. All other findings occurred either individually or were biologically equally distributed over control and treatment groups. They were considered to be incidental or spontaneous in origin and without any relation to treatment.
The stages of spermatogenesis in the testes of males of the high dose test group were comparable to those of the controls. In the ovaries of control and high dose females the different stages of functional bodies (especially corpora lutea) were present and normal. - Histopathological findings: neoplastic:
- no effects observed
- Other effects:
- no effects observed
- Description (incidence and severity):
- Thyroid hormones
In parental males (test groups 1, 2 and 3; 5, 25 and 75 mg/kg bw/d) and in male and female pups at PND13 (test groups 11, 12 and 13; 5, 25 and 75 mg/kg bw/d), no treatment-related alterations of T4 levels (thyroid hormones) were observed. - Reproductive function: oestrous cycle:
- no effects observed
- Description (incidence and severity):
- Estrous cycle data revealed regular cycles in the parental females of all test groups including the control. The mean estrous cycle duration in the different test groups (0-3) was between 3.97 and 4.03 days.
- Reproductive function: sperm measures:
- not examined
- Reproductive performance:
- no effects observed
- Description (incidence and severity):
- For all F0 parental males, which were placed with females to generate F1 pups, copulation was confirmed. Thus, the male mating index was 100 % in all test groups. Fertility was proven for most of the F0 parental males within the scheduled mating interval for F1 litter.
One mid-dose male and one high-dose male did not generate pregnancy. Thus, the male fertility index ranged between 90 % and 100 % without showing any relation to dosing. This reflects the normal range of biological variation inherent in the strain of rats used for this study.
The apparently infertile mid-dose male did not show relevant gross lesions, while high-dose male showed a yellow focus (12 mm in diameter) in the left epididymis
The female mating index calculated after the mating period for F1 litter was 100 % in all test groups. The mean duration until sperm was detected (GD 0) varied between 1.9 and 2.4 days without any relation to dosing.The fertility index varied between 90 % in test groups 2 and 3 and 100 % in test groups 0 and 1. These values reflect the normal range of biological variation inherent in the strain of rats used for this study.
The non-pregnant mid-dose female had no relevant gross lesions or histopathological findings, while high-dose female showed a moderate atrophy of the vagina squamous epithelium with a slightly increased mucification.
The mean duration of gestation was similar in all test groups (i.e. between 22.0 and 22.2 days).
One mid-dose female, which was sperm-positive showed only implantation sites at necropsy, but did not deliver (i.e. this dam was pregnant by stain). Therefore, the gestation index was 88.9 % in test group 2, but reached 100 % in all other test groups. Furthermore, the postimplantation loss value was 17.4 % in test group 2, but was 5.6 %, 6.7 % and 3.0% in test groups 0, 1 and 3. The increased resorption rate at the mid-dose is considered to be incidental due to its isolated occurrence and lack of dose-response relationship.
Implantation was not affected by the treatment since the mean number of implantation sites was comparable between all test substance-treated groups and the control, taking normal biological variation into account (12.5 / 13.1 / 11.0 and 11.4 implants/dam in test groups 0-3, respectively). Furthermore, there were no indications for any test substance-induced intrauterine embryo-/fetolethality since the post-implantation loss did not show any significant differences between the groups, and the mean number of F1 pups delivered per dam remained unaffected (11.8 / 12.2 / 11.4 and 11.1 pups/dam in test groups 0-3, respectively).
The rate of liveborn pups was also not affected by the test substance, as indicated by live birth indices of 98.3 % / 100 % / 100 % and 97.0 % in test groups 0-3. Moreover, the number of stillborn pups was not significantly different between the test groups. All values are well covered by the historical control range. Thus, the test substance did not adversely affect reproduction and delivery of the F0 generation parental females. - Key result
- Dose descriptor:
- NOAEL
- Effect level:
- 75 mg/kg bw/day
- Based on:
- test mat.
- Sex:
- male/female
- Basis for effect level:
- reproductive performance
- other: fertility
- Key result
- Critical effects observed:
- no
- Clinical signs:
- no effects observed
- Description (incidence and severity):
- There were no test substance-related adverse clinical signs observed in any of the F1 generation pups of the different test groups.
- Mortality / viability:
- mortality observed, non-treatment-related
- Description (incidence and severity):
- The viability index indicating pup survival during early lactation (PND 0-4) varied between 98.1 % / 98.5 % / 100 % and 98.4 % in test groups 0-3 without showing any association to the treatment. The survival index indicating pup mortality on PND 4-13 was 100 % in all test groups.
- Body weight and weight changes:
- effects observed, treatment-related
- Description (incidence and severity):
- Mean body weights of the F1 male and female pups of test group 3 (75 mg/kg bw/d) were statistically significantly decreased from PND 7 onwards until scheduled sacrifice on PND 13 (about 10 % below control, both sexes combined). The mean body weight change of the high-dose male and female F1 pups (and both sexes combined) was statistically significantly decreased during PND 1-7 (up to 19% below control, both sexes combined) and if calculated for the entire lactation period (PND 1-13; 11 % below control, both sexes combined). Furthermore, the mean body weight change of the high-dose male pups was statistically significantly reduced during PND 7-13 (10 % below control). The decrease in body weight (change) indicates a delayed body weight development of high-dose male and female F1 pups. Therefore, it was assessed as treatment-related and adverse.
Mean body weights and body weight change of all male and female F1 pups in test groups 1 and 2 (5 and 25 mg/kg bw/d) were comparable to the concurrent control values throughout the entire lactation period. One female runt was seen, each, in the control and in test group 3 (75 mg/kg bw/d). - Food efficiency:
- not examined
- Ophthalmological findings:
- not examined
- Urinalysis findings:
- not examined
- Sexual maturation:
- not examined
- Organ weight findings including organ / body weight ratios:
- not examined
- Other effects:
- no effects observed
- Description (incidence and severity):
- Anogenital distance/anogenital index:
Neither on anogenital distance nor anogenital index test substance-related effects were noted in all test substance-treated F1 male and female pups (test groups 1-3; 5, 25 or 75 mg/kg bw/d]).
Nipple/ areola anlagen
The apparent number and percentage of male pups having areolae was not influenced by the test substance when examined on PND 13.
Pup necropsy observations
A few F1 pups showed spontaneous findings at gross necropsy, such as small testis, dilated renal pelvis, hydronephrosis and hydroureter. These findings occurred without any relation to dosing and are considered to be spontaneous in nature. - Behaviour (functional findings):
- not examined
- Developmental immunotoxicity:
- not examined
- Key result
- Dose descriptor:
- NOAEL
- Generation:
- F1
- Effect level:
- 25 mg/kg bw/day
- Based on:
- test mat.
- Sex:
- male/female
- Basis for effect level:
- body weight and weight gain
- Key result
- Dose descriptor:
- LOAEL
- Effect level:
- 75 mg/kg bw/day
- Based on:
- test mat.
- Sex:
- male/female
- Basis for effect level:
- body weight and weight gain
- Key result
- Critical effects observed:
- no
- Key result
- Reproductive effects observed:
- no
- Lowest effective dose / conc.:
- 75 mg/kg bw/day
- Treatment related:
- no
- Conclusions:
- Under the conditions of the present OECD 422 combined repeated dose toxicity study with the reproductive/developmental screening test in Wistar rats, the NOAEL (no observed adverse effect level) for general, systemic toxicity of (+)-3-Aminomethylpinan was the mid dose of 25 mg/kg bw/d. At the highest tested dose of 75 mg/kg bw/d, treatment-related adverse effects were observed based on a reduction in food consumption and a decrease in body weight (change) of male and female F0 parental animals. The NOAEL for reproductive performance and fertility of the F0 parental animals was the highest tested dose of 75 mg/kg bw/d. The NOAEL for developmental toxicity in the F1 offspring was 25 mg/kg bw/d due to a probable delay in body weight development of F1 male and female pups at 75 mg/kg bw/d.
- Executive summary:
(+)-3-Aminomethylpinan was administered daily as an aqueous preparation to groups of 10 male and 10 female Wistar rats (F0 animals) by gavage at doses of 5, 25 and 75 mg/kg body weight/day (mg/kg bw/d). Control animals (10 male and 10 female Wistar rats) were dosed daily with the vehicle only (0.5% Sodium carboxymethyl cellulose with 5 mg/100 ml Tween 80 suspension in drinking water). The duration of treatment covered a 2-week pre-mating and a mating period in both sexes, one day post-mating in males, and the entire gestation period as well as up to 22 days of the lactation period in females. After 2 weeks of premating treatment the F0 animals were mated to produce F1 generation pups. Mating pairs were from the same test group. Mating was discontinued as soon as sperm were detected in the vaginal smear. F0 animals were examined for their reproductive performance including determination of the number of implantation sites and the calculation of postimplantation loss for all F0 females. A detailed clinical observation (DCO) was performed in all animals before initial test substance administration and, as a rule, thereafter at weekly intervals. Food consumption of the F0 parents was determined once weekly during premating. In dams, food consumption was determined for gestation days (GD) 0-7, 7-14, 14-20 and postnatal days (PND) 1-4, 4-7, 7-10 and 10-13. Body weights of F0 parents were determined once a week, in males throughout the study and in females during premating. During gestation and lactation period, F0 females were weighed on GD 0, 7, 14 and 20, on the day of parturition (PND 0) and on PND 4, 7, 10 and 13. Estrous cycle data were evaluated for F0 generation females over a two-week period prior to mating until evidence of mating occurred. Moreover, the estrous stage of each female was determined on the day of scheduled sacrifice. The pups were sexed and examined for macroscopically evident changes on PND 0. They were weighed on PND 1, 4, 7 and 13. Their viability was recorded. At necropsy on PND 4 and 13, all pups were sacrificed with CO2, under isoflurane anesthesia, and examined macroscopically for external and visceral findings. Anogenital distance (defined as the distance from the anus [center of the anal opening] to the base of the genital tubercle) measurements were conducted in a blind randomized fashion, using a measuring ocular on all live male and female pups on PND 1. All surviving male pups were examined for the presence or absence of nipple/areola anlagen on PND 13. The number of nipple/areola anlagen were counted. Clinico-chemical and hematological examinations were performed in 5 animals per sex and group towards the end of the administration period. Blood samples from all dams at PND 14 and all males at termination were taken by puncturing the retrobulbar venous plexus under isoflurane anesthesia for hormone measurement. Blood samples were taken from all surplus pups at PND 4 as well as one male and one female pup per litter at PND 13 by decapitation under isoflurane anesthesia for hormone measurement. At the end of the administration period a functional observational battery was performed and motor activity was measured in 5 parental males and females per group. All F0 parental animals were sacrificed by decapitation, under isoflurane anesthesia, and were assessed by gross pathology. Weights of selected organs were recorded and a histopathological examination was performed.
The following test substance-related adverse effects/findings were noted:
Test group 3 (75 mg/kg bw/d):
F0 PARENTAL ANIMALS / CLINICAL EXAMINATIONS/ REPRODUCTIVE PERFORMANCE/ CLINICAL PATHOLOGY/ PATHOLOGY
F0 males:
- Statistically significantly reduced food consumption during premating days 0-7 (-10%) and 0-13 (-8%)
- Statistically significantly decreased body weight change during premating days 0-7 (-85% below control), days 0-13 (-49%) and during mating (without statistical significance, -24%).
F0 females:
- Statistically significantly reduced food consumption during premating days 0-7 (-8%) and PND 4-7 (-11%)
- Body weight loss and a decrease of body weight change (-5.8 g) without statistical significance during PND 0-4 (lactation period)
F1 PUPS / CLINICAL EXAMINATIONS/ GROSS FINDINGS
- Statistically significantly decreased pup body weight on PND 1-13 (about 10% below control on PND 13, both sexes combined)
- Statistically significantly decreased pup body weight change on PND 1-7 (up to 19% below control, both sexes combined) and PND 1-13 (11% below control, both sexes combined)
Test groups 2 and 1 (25 and 5 mg/kg bw/d)
F0 PARENTAL ANIMALS / CLINICAL EXAMINATIONS/ REPRODUCTIVE PERFORMANCE/ CLINICAL PATHOLOGY/PATHOLOGY
- No test substance-related adverse findings
F1 PUPS / CLINICAL EXAMINATIONS/ GROSS FINDINGS
- No test substance-related adverse findings
Reference
Table 1: Summary food consumption per animal and day
|
Test Group 0 0 mg/kg bw/d |
Test Group 1 5 mg/kg bw/d |
Test Group 2 25 mg/kg bw/d |
Test Group 3 75 mg/kg bw/d |
|
Male, premating |
|||||
d0 - 7 |
Mean [g] |
21.8 n |
21.6 |
20.9 |
19.6 ** |
S.D. |
1.5 |
1.6 |
1.0 |
1.1 |
|
Deviation vs Control [%] |
|
-0.8 |
-4.2 |
-9.9 |
|
d7 - 13 |
Mean [g] |
22.3 n |
22.2 |
22.1 |
21.1 |
S.D. |
1.1 |
2.0 |
1.1 |
0.8 |
|
Deviation vs Control [%] |
|
-0.4 |
-0.9 |
-5.2 |
|
d0 - 13 |
Mean [g] |
22.0 n |
21.9 |
21.4 |
20.3* |
S.D. |
1.3 |
1.7 |
1.0 |
0.9 |
|
Deviation vs Control [%] |
|
-0.6 |
-2.7 |
-7.0 |
|
Female, premating |
|||||
d0 - 7 |
Mean [g] |
14.1 n |
14.4 |
14.2 |
13.0 * |
S.D. |
0.7 |
0.7 |
1.1 |
0.9 |
|
Deviation vs Control [%] |
|
2.0 |
0.5 |
-8.1 |
|
d7 - 13 |
Mean [g] |
14.4 n |
14.8 |
14.8 |
14.5 |
S.D. |
0.9 |
0.7 |
1.4 |
1.1 |
|
No of animals |
10 |
10 |
10 |
10 |
|
Deviation vs Control [%] |
|
2.7 |
2.3 |
0.5 |
|
d0 - 13 |
Mean [g] |
14.3 n |
14.6 |
14.4 |
13.7 |
S.D. |
0.7 |
0.7 |
1.2 |
1.0 |
|
No of animals |
10 |
10 |
10 |
10 |
|
Deviation vs Control [%] |
|
2.3 |
1.3 |
-4.1 |
|
Female, gestation |
|||||
d0 - 7 |
Mean [g] |
18.4 n |
18.9 |
19.1 |
18.5 |
S.D. |
1.7 |
1.1 |
2.1 |
2.0 |
|
Deviation vs Control [%] |
|
2.3 |
3.8 |
0.5 |
|
d7 - 14 |
Mean [g] |
21.2 n |
20.2 |
21.2 |
19.7 |
S.D. |
2.6 |
1.5 |
2.5 |
1.3 |
|
Deviation vs Control [%] |
|
-4.7 |
0.1 |
-7.2 |
|
d14 - 20 |
Mean [g] |
21.5 n |
21.5 |
22.2 |
21.1 |
S.D. |
2.1 |
0.9 |
2.5 |
1.1 |
|
Deviation vs Control [%] |
|
-0.1 |
3.3 |
-2.2 |
|
d0 - 20 |
Mean [g] |
20.3 n |
20.1 |
20.8 |
19.7 |
S.D. |
2.0 |
1.1 |
2.1 |
1.1 |
|
Deviation vs Control [%] |
|
-1.019.1 |
2.3 |
-3.2 |
|
Female, lactation |
|||||
d1 - 4 |
Mean [g] |
29.1 n |
31.8 |
27.7 |
25.2 |
S.D. |
3.6 |
3.9 |
5.4 |
4.4 |
|
Deviation vs Control [%] |
|
9.3 |
-4.9 |
-13.6 |
|
d4 – 7 |
Mean [g] |
38.1 n |
40.4 |
37.1 |
34.1 * |
S.D. |
2.4 |
3.4 |
3.9 |
3.7 |
|
Deviation vs Control [%] |
|
6.1 |
-2.5 |
-10.6 |
|
d7 - 10 |
Mean [g] |
46.1 n |
48.7 |
45.5 |
42.1 |
S.D. |
2.9 |
4.7 |
3.9 |
3.1 |
|
Deviation vs Control [%] |
|
5.6 |
-1.4 |
-8.7 |
|
d10 - 13 |
Mean [g] |
55.2 n |
55.8 |
52.9 |
51.2 |
S.D. |
3.6 |
3.9 |
5.1 |
3.3 |
|
Deviation vs Control [%] |
|
1.0 |
-4.2 |
-7.4 |
|
d1 - 13 |
Mean [g] |
42.1 n |
44.2 |
40.8 |
38.3 |
S.D. |
2.6 |
3.6 |
4.2 |
3.3 |
|
Deviation vs Control [%] |
|
4.9 |
-3.1 |
-9.0 |
|
Statistic Profile = Dunnett test (two-sided), * p<=0.05, ** p <=0.01, d = day; n=DUNNETT |
Table 2: Summary changes body weights
|
Test Group 0 0 mg/kg bw/d |
Test Group 1 5 mg/kg bw/d |
Test Group 2 25 mg/kg bw/d |
Test Group 3 75 mg/kg bw/d |
|
Male, premating |
|||||
d0 - 7 |
Mean [g] |
11.8 n |
12.0 |
8.1 |
1.8 ** |
S.D. |
5.2 |
6.5 |
4.8 |
4.8 |
|
d7 - 13 |
Mean [g] |
13.1 n |
9.8 |
12.2 |
11.0 |
S.D. |
5.1 |
6.3 |
5.2 |
5.4 |
|
d0 - 13 |
Mean [g] |
25.0 n |
21.8 |
20.3 |
12.8 ** |
S.D. |
6.9 |
11.0 |
6.4 |
7.9 |
|
Male, mating |
|||||
d7 - 14 |
Mean [g] |
10.8 n |
10.4 |
11.1 |
8.2 |
S.D. |
4.4 |
3.0 |
4.4 |
2.7 |
|
Female, premating |
|||||
d0 - 7 |
Mean [g] |
-0.8 n |
0.5 |
5.2 |
1.1 |
S.D. |
9.3 |
6.6 |
7.5 |
5.9 |
|
d7 - 13 |
Mean [g] |
6.9 n |
3.5 |
2.4 |
3.7 |
S.D. |
5.5 |
7.5 |
6.9 |
6.1 |
|
d0 - 13 |
Mean [g] |
6.1 n |
4.0 |
7.7 |
4.8 |
S.D. |
5.2 |
4.0 |
6.0 |
3.9 |
|
Female, gestation |
|||||
d0 - 7 |
Mean [g] |
26.3 n |
26.6 |
29.8 |
25.4 |
S.D. |
6.5 |
5. |
7.1 |
5.0 |
|
d7 - 14 |
Mean [g] |
30.6 n |
27.3 |
26.6 |
29.8 |
S.D. |
4.8 |
3.7 |
6.4 |
5.0 |
|
d14 - 20 |
Mean [g] |
58.2 n |
60.8 |
51.4 |
55.7 |
S.D. |
10.1 |
8.9 |
20.6 |
10.7 |
|
d0 - 20 |
Mean [g] |
115.1 n |
114.7 |
107.8 |
111.0 |
S.D. |
16.4 |
8.6 |
28.6 |
14.5 |
|
Female, lactation |
|||||
d1 - 4 |
Mean [g] |
3.9 n |
7.3 |
2.7 |
-5.8 |
S.D. |
7.8 |
13.4 |
12.0 |
10.9 |
|
d4 – 7 |
Mean [g] |
4.5 n |
9.4 |
7.7 |
9.6 |
S.D. |
7.6 |
8.2 |
2.6 |
7.6 |
|
d7 - 10 |
Mean [g] |
12.9 n |
10.5 |
9.7 |
11.9 |
S.D. |
7.4 |
4.2 |
5.4 |
5.0 |
|
d10 - 13 |
Mean [g] |
4.8 n |
3.0 |
5.0 |
7.7 |
S.D. |
4.9 |
7.0 |
6.2 |
7.5 |
|
d1 - 13 |
Mean [g] |
26.1 n |
30.1 |
25.2 |
23.4 |
S.D. |
8.6 |
12.9 |
10.0 |
6.7 |
|
Statistic Profile = Dunnett test (two-sided), * p<=0.05, ** p <= 0.01, d = day; n=DUNNETT |
Table 3: Summary pup report body weights
|
Test Group 0 0 mg/kg bw/d |
Test Group 1 5 mg/kg bw/d |
Test Group 2 25 mg/kg bw/d |
Test Group 3 75 mg/kg bw/d |
|
d1 Runt |
Males |
0 |
0 |
0 |
0 |
Females |
1 |
0 |
0 |
1 |
|
Day 1 |
|||||
Males |
Mean [g] |
6.7 n |
6.9 |
6.9 |
6.4 |
S.D. |
0.4 |
0.7 |
0.6 |
0.5 |
|
Deviation vs Control [%] |
|
2.7 |
2.6 |
-4.1 |
|
Females |
Mean [g] |
6.5 n |
6.5 |
6.5 |
6.3 |
S.D. |
0.5 |
0.6 |
0.3 |
0.5 |
|
Deviation vs Control [%] |
|
0.4 |
0.2 |
-3.0 |
|
Males + Females |
Mean [g] |
6.6 n |
6.6 |
6.7 |
6.3 |
S.D. |
0.4 |
0.6 |
0.5 |
0.5 |
|
Deviation vs Control [%] |
|
1.1 |
2.1 |
-3.4 |
|
Day 4 |
|||||
Males |
Mean [g] |
10.2 n |
10.4 |
10.3 |
9.3 |
S.D. |
0.5 |
1.1 |
1.0 |
0.8 |
|
Deviation vs Control [%] |
|
1.4 |
1.1 |
-8.6 |
|
Females |
Mean [g] |
10.1 n |
9.9 |
9.9 |
9.2 |
S.D. |
0.8 |
1.1 |
0.7 |
0.8 |
|
Deviation vs Control [%] |
|
-1.6 |
-1.8 |
-8.6 |
|
Males + Females |
Mean [g] |
10.1 n |
10.1 |
10.2 |
9.3 |
S.D. |
0.6 |
1.1 |
0.9 |
0.7 |
|
Deviation vs Control [%] |
|
-0.4 |
0.3 |
-8.5 |
|
Day 7 |
|||||
Males |
Mean [g] |
16.5 n |
16.8 |
16.7 |
14.8 * |
S.D. |
0.6 |
1.7 |
1.3 |
1.4 |
|
Deviation vs Control [%] |
|
1.8 |
1.0 |
-10.3 |
|
Females |
Mean [g] |
16.2 n |
16.0 |
15.9 |
14.6 * |
S.D. |
0.7 |
1.7 |
1.0 |
1.2 |
|
Deviation vs Control [%] |
|
-0.8 |
-1.5 |
-9.5 |
|
Males + Females |
Mean [g] |
16.3 n |
16.4 |
16.4 |
14.7 * |
S.D. |
0.6 |
1.7 |
1.2 |
1.1 |
|
Deviation vs Control [%] |
|
0.4 |
0.4 |
-9.7 |
|
Day 13 |
|||||
Males |
Mean [g] |
30.8 n |
31.5 |
30.9 |
27.6 ** |
S.D. |
1.8 |
2.6 |
1.7 |
2.4 |
|
Deviation vs Control [%] |
|
2.0 |
0.2 |
-10.5 |
|
Females |
Mean [g] |
30.2 n |
30.4 |
30.1 |
27.5 * |
S.D. |
1.4 |
2.4 |
1.0 |
2.3 |
|
Deviation vs Control [%] |
|
0.8 |
-0.5 |
-9.0 |
|
Males + Females |
Mean [g] |
30.5 n |
30.9 |
30.6 |
27.6 ** |
S.D. |
1.6 |
2.5 |
1.6 |
2.2 |
|
Deviation vs Control [%] |
|
12 |
0.1 |
-9.7 |
|
Statistic Profile = Dunnett test (two-sided), * p<=0.05, ** p <=0.01, d = day; n=DUNNETT |
Table 4: Summary Pup Changes Body Weights
|
Test Group 0 0 mg/kg bw/d |
Test Group 1 5 mg/kg bw/d |
Test Group 2 25 mg/kg bw/d |
Test Group 3 75mg/kg bw/d |
|
d1 - 4 |
|||||
Male |
Mean [g] |
3.5 n |
3.5 |
3.5 |
2.9 * |
S.D. |
0.4 |
0.5 |
0.5 |
0.3 |
|
Female |
Mean [g] |
3.6 n |
3.4 |
3.4 |
2.9 * |
S.D. |
0.5 |
0.6 |
0.4 |
0.3 |
|
Male + Female |
Mean [g] |
3.6 n |
3.5 |
3.5 |
2.9 * |
S.D. |
0.4 |
0.6 |
0.4 |
0.3 |
|
d4 – 7 |
|||||
Male |
Mean [g] |
6.3 n |
6.4 |
6.3 |
5.4 * |
S.D. |
0.6 |
0.8 |
0.6 |
0.7 |
|
Female |
Mean [g] |
6.1 n |
6.1 |
6.1 |
5.4 * |
S.D. |
0.6 |
0.7 |
0.5 |
0.6 |
|
Male + Female |
Mean [g] |
6.2 n |
6.2 |
6.2 |
5.4 * |
S.D. |
0.6 |
0.7 |
0.6 |
0.6 |
|
d7 - 13 |
|||||
Male |
Mean [g] |
14.3 n |
14.7 |
14.2 |
12.8 * |
S.D. |
1.5 |
1.2 |
0.6 |
1.7 |
|
Female |
Mean [g] |
14.0 n |
14.4 |
14.1 |
12.8 |
S.D. |
1.3 |
1.2 |
0.6 |
1.4 |
|
Male + Female |
Mean [g] |
14.2 n |
14.5 |
14.2 |
12.8 |
S.D. |
1.4 |
1.2 |
0.7 |
1.5 |
|
d1 - 13 |
|||||
Male |
Mean [g] |
24.2 n |
24.6 |
24.0 |
21.1 ** |
S.D. |
1.8 |
2.2 |
1.4 |
2.2 |
|
Female |
Mean [g] |
23.7 n |
23.9 |
23.6 |
21.2 ** |
S.D. |
1.4 |
2.2 |
0.9 |
2.0 |
|
Male + Female |
Mean [g] |
23.9 n |
24.2 |
23.9 |
21.2 ** |
S.D. |
1.7 |
2.2 |
1.3 |
2.0 |
|
Statistic Profile = Dunnett test (two-sided), * p<=0.05, ** p <=0.01, d = day; n=DUNNETT |
Effect on fertility: via oral route
- Endpoint conclusion:
- no adverse effect observed
- Dose descriptor:
- NOAEL
- 75 mg/kg bw/day
- Study duration:
- subchronic
- Species:
- rat
- Quality of whole database:
- Klimisch code 1, guideline conform study under GLP.
Additional information
The test substance was assessed in a combined repeated dose toxicity study with the reproductive and developmental screening test according to OECD Guideline 422 (BASF SE, 2017). The test substance was administered daily as an aqueous preparation to groups of 10 male and 10 female Wistar rats (F0 animals) by gavage at doses of 5, 25 and 75 mg/kg bodyweight/day (mg/kg bw/d). Control animals (10 male and 10 female Wistar rats) were dosed daily with the vehicle only (0.5% Sodium carboxymethyl cellulose with 5 mg/100 mL Tween 80 suspension in drinking water). The duration of treatment covered a 2-week pre-mating and a mating period in both sexes, one day post-mating in males, and the entire gestation period as well as up to 22 days of the lactation period in females.
After 2 weeks of premating treatment, the F0 animals were mated to produce F1 generation pups. Mating pairs were from the same test group. Mating was discontinued as soon as sperm were detected in the vaginal smear. F0 animals were examined for their reproductive performance including determination of the number of implantation sites and the calculation of postimplantation loss for all F0 females. A detailed clinical observation (DCO) was performed in all animals before initial test substance administration and thereafter at weekly intervals. Food consumption of the F0 parents was determined once weekly during premating. In dams, food consumption was determined for gestation days (GD) 0-7, 7-14, 14-20 and postnatal days (PND) 1-4, 4-7, 7-10 and 10-13. Body weights of F0 parents were determined once a week, in males throughout the study and in females during premating. During gestation and lactation period, F0 females were weighed on GD 0, 7, 14 and 20, on the day of parturition (PND 0) and on PND 4, 7, 10 and 13. Estrous cycle data were evaluated for F0 generation females over a two-week period prior to mating until evidence of mating occurred. Moreover, the estrous stage of each female was determined on the day of scheduled sacrifice. The pups were sexed and examined for macroscopically evident changes on PND 0. They were weighed on PND 1, 4, 7 and 13. Their viability was recorded. At necropsy on PND 4 and 13, all pups were sacrificed with CO2, under isoflurane anesthesia, and examined macroscopically for external and visceral findings.
Anogenital distance measurements were conducted in a blind randomized fashion on PND 1. All surviving male pups were examined for the presence or absence of nipple/areola anlagen on PND 13. Clinico-chemical and hematological examinations were performed in 5 animals per sex and group towards the end of the administration period. Blood samples from all dams at PND 14 and all males at termination were taken for hormone measurement. Blood samples were taken from all surplus pups at PND 4 as well as one male and one female pup per litter at PND 13 for hormone measurement. At the end of the administration period a functional observational battery was performed and motor activity was measured in 5 parental males and females per group. All F0 parental animals were assessed by gross pathology. Weights of selected organs were recorded and a histopathological examination was performed.
In the 5 and 25 mg/kg bw/day dose group, no test substance-related adverse findings were observed in F0 parental animals or F1 pups. In the 75 mg/kg bw/dy dose group, a statistically significantly reduced food consumption during premating days 0-7 was observed in both sexes, as well as a statistically significantly decreased body weight change during premating days 0-7 in males. Furthermore, a statistically significantly decreased pup bodyweight and weight change on PND 1-13 was observed (both sexes combined) in F1 pups.
Under the conditions of the present OECD 422 combined repeated dose toxicity study with the reproductive/developmental screening test in Wistar rats, the NOAEL (no observed adverse effect level) for general, systemic toxicity of the test substance was the mid dose of 25 mg/kg bw/d. At the highest tested dose treatment-related adverse effects were observed based on a reduction in food consumption and a decrease in body weight (change) of male and female F0 parental animals. The NOAEL for reproductive performance and fertility of the F0 parental animals was the highest tested dose of 75 mg/kg bw/d. The NOAEL for developmental toxicity in the F1 offspring was 25 mg/kg bw/d due to a delay in body weight development of F1 male and female pups at 75 mg/kg bw/d.
Effects on developmental toxicity
Description of key information
In a reproductive screening test according to OECD Guideline 422, a NOAEL for developmental toxicity in the F1 offspring was 25 mg/kg bw/d due to a delay in body weight development of F1 male and female pups at 75 mg/kg bw/d.
Effect on developmental toxicity: via oral route
- Endpoint conclusion:
- adverse effect observed
- Dose descriptor:
- NOAEL
- 25 mg/kg bw/day
- Study duration:
- subacute
- Species:
- rat
Justification for classification or non-classification
Classification, Labeling, and Packaging Regulation (EC) No 1272/2008
The available experimental test data are reliable and suitable for classification purposes under Regulation 1272/2008.
As a result the substance is not considered to be classified for toxicity for reproduction under Regulation (EC) No. 1272/2008, as amended for the tenth time in Regulation (EU) No 2017/776.
Additional information
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