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EC number: 817-187-7 | CAS number: 1803088-15-4
- Life Cycle description
- Uses advised against
- Endpoint summary
- Appearance / physical state / colour
- Melting point / freezing point
- Boiling point
- Density
- Particle size distribution (Granulometry)
- Vapour pressure
- Partition coefficient
- Water solubility
- Solubility in organic solvents / fat solubility
- Surface tension
- Flash point
- Auto flammability
- Flammability
- Explosiveness
- Oxidising properties
- Oxidation reduction potential
- Stability in organic solvents and identity of relevant degradation products
- Storage stability and reactivity towards container material
- Stability: thermal, sunlight, metals
- pH
- Dissociation constant
- Viscosity
- Additional physico-chemical information
- Additional physico-chemical properties of nanomaterials
- Nanomaterial agglomeration / aggregation
- Nanomaterial crystalline phase
- Nanomaterial crystallite and grain size
- Nanomaterial aspect ratio / shape
- Nanomaterial specific surface area
- Nanomaterial Zeta potential
- Nanomaterial surface chemistry
- Nanomaterial dustiness
- Nanomaterial porosity
- Nanomaterial pour density
- Nanomaterial photocatalytic activity
- Nanomaterial radical formation potential
- Nanomaterial catalytic activity
- Endpoint summary
- Stability
- Biodegradation
- Bioaccumulation
- Transport and distribution
- Environmental data
- Additional information on environmental fate and behaviour
- Ecotoxicological Summary
- Aquatic toxicity
- Endpoint summary
- Short-term toxicity to fish
- Long-term toxicity to fish
- Short-term toxicity to aquatic invertebrates
- Long-term toxicity to aquatic invertebrates
- Toxicity to aquatic algae and cyanobacteria
- Toxicity to aquatic plants other than algae
- Toxicity to microorganisms
- Endocrine disrupter testing in aquatic vertebrates – in vivo
- Toxicity to other aquatic organisms
- Sediment toxicity
- Terrestrial toxicity
- Biological effects monitoring
- Biotransformation and kinetics
- Additional ecotoxological information
- Toxicological Summary
- Toxicokinetics, metabolism and distribution
- Acute Toxicity
- Irritation / corrosion
- Sensitisation
- Repeated dose toxicity
- Genetic toxicity
- Carcinogenicity
- Toxicity to reproduction
- Specific investigations
- Exposure related observations in humans
- Toxic effects on livestock and pets
- Additional toxicological data
![](https://echa.europa.eu/o/diss-blank-theme/images/factsheets/A-REACH/factsheet/print_toxicological-information.png)
Repeated dose toxicity: oral
Administrative data
- Endpoint:
- short-term repeated dose toxicity: oral
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- guideline study
Data source
Reference
- Reference Type:
- study report
- Title:
- Unnamed
- Year:
- 2 016
Materials and methods
Test guidelineopen allclose all
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 422 (Combined Repeated Dose Toxicity Study with the Reproduction / Developmental Toxicity Screening Test)
- Version / remarks:
- 2016
- Qualifier:
- according to guideline
- Guideline:
- other: EPA OPPTS 870.3650, Combined Repeated Dose Toxicity Study with the Reproduction/Developmental Toxicity Screening Test, 2000.
- Version / remarks:
- 2000
- GLP compliance:
- yes (incl. QA statement)
- Limit test:
- yes
Test material
- Reference substance name:
- 5,7-Di-t-butyl-3-[3,5-dimethyl-4-[(1,3,7,9-tetra-t-butyl-5-methyl-5H-benzo[d][1,3,2]benzodioxaphosphocin-11-yl)oxy]phenyl]-3H-benzofuran-2-one
- EC Number:
- 817-187-7
- Cas Number:
- 1803088-15-4
- Molecular formula:
- C54 H73 O5 P
- IUPAC Name:
- 5,7-Di-t-butyl-3-[3,5-dimethyl-4-[(1,3,7,9-tetra-t-butyl-5-methyl-5H-benzo[d][1,3,2]benzodioxaphosphocin-11-yl)oxy]phenyl]-3H-benzofuran-2-one
- Details on test material:
- - State of aggregation: Solid / white
- Storage Condition: room temperature under light exclusion
Constituent 1
Test animals
- Species:
- rat
- Strain:
- Wistar
- Details on species / strain selection:
- The Wistar Han rat was chosen as the animal model for this study as it is an accepted rodent species for toxicity testing by regulatory agencies.
- Sex:
- male/female
- Details on test animals or test system and environmental conditions:
- TEST ANIMALS
- Source: Charles River Deutschland, Sulzfeld, Germany
- Females (if applicable) nulliparous and non-pregnant: yes
- Age at study initiation: males were 10-12 weeks old and females were 12-14 weeks old.
- Weight at study initiation: males weighed between 246 and 312 g and females weighed between 204 and 246 g.
- Housing: On arrival and following the pretest (females only) and pre-mating period, Main animals were group housed (up to 5 animals of the same sex and same dosing group together) in polycarbonate cages (Macrolon, MIV type, height 18 cm). Recovery males and females were housed as such during the entire study period. During the mating phase, Main males and females were cohabitated on a 1:1 basis in Macrolon plastic cages (MIII type, height 18 cm). During the post-mating phase, Main males were housed in their home cage (Macrolon plastic cages, MIV type, height 18 cm) with a maximum of 5 males/cage. Main Females were individually housed in Macrolon plastic cages (MIII type, height 18 cm). During the lactation phase, Main females were housed in Macrolon plastic cages (MIII type, height 18 cm). Pups were housed with the dam, except during locomotor activity monitoring of the dams, when the pups were kept warm in their home cage using bottles filled with warm water. In order to avoid hypothermia of pups, pups were not be left without their dam or a bottle filled with warm water for longer than 30-40 minutes. During locomotor activity monitoring, animals were housed individually in a Hi-temp polycarbonate cage (Ancare corp., USA; dimensions: 48.3 x 26.7 x 20.3 cm) without cageenrichment, bedding material, food and water. The cages containing appropriate bedding (Lignocel S 8-15, JRS - J.Rettenmaier & Söhne GmbH + CO. KG, Rosenberg, Germany) equipped with water bottles.
- Diet: Pelleted rodent diet (SM R/M-Z from SSNIFF® Spezialdiäten GmbH, Soest, Germany) was provided ad libitum throughout the study, except during designated procedures. During motor activity measurements, animals had no access to food for a maximum of 2 hours.
- Water: Municipal tap water was freely available to each animal via water bottles.
- Acclimation period: 5 days prior to start of the pretest period (females) or 5 days before the commencement of dosing (males)
DETAILS OF FOOD AND WATER QUALITY:
The feed was analyzed by the supplier for nutritional components and environmental contaminants. Results of the analysis were provided by the supplier and are on file at the Test Facility. It is considered that there were no known contaminants in the feed that would interfere with the objectives of the study. Periodic analysis of the water is performed, and results of these analyses are on file at the Test Facility. It is considered that there were no known contaminants in the water that would interfere with the objectives of the study.
ENVIRONMENTAL CONDITIONS
- Temperature (°C): 19 to 22
- Humidity (%): 45-71
- Air changes (per hr): ≥10
- Photoperiod (hrs dark / hrs light): 12/12
Administration / exposure
- Route of administration:
- oral: gavage
- Vehicle:
- corn oil
- Details on oral exposure:
- PREPARATION OF DOSING SOLUTIONS:
Test item dosing formulations (w/w) were homogenized to visually acceptable levels at appropriate concentrations to meet dose level requirements. The dosing formulations were prepared daily, were protected from light and dosed within 5 hours after adding the vehicle to the test item. Test item dosing formulations were kept at room temperature until dosing. If practically possible, the dosing formulations and vehicle were continuously stirred until and during dosing. Adjustment was made for specific gravity of the vehicle. No correction was made for the purity/composition of the test item.
VEHICLE
- Justification for use and choice of vehicle (if other than water):
Trial preparations were performed at the Test Facility prior to conduct of the Dose Range Finding Study to select the suitable vehicle and to establish a suitable formulation procedure. Ultimately, the vehicle (corn oil) was selected by the Sponsor, i.e. the same vehicle as used in the Dose Range Finding Study.
- Concentration in vehicle: 25, 75, 250 mg/kg
- Amount of vehicle (if gavage): 4 ml/kg - Analytical verification of doses or concentrations:
- yes
- Details on analytical verification of doses or concentrations:
- In the Group 1 formulation (control group), no test item was detected. The concentrations analyzed in the formulations of Groups 2, 3 and 4 were in agreement with the target concentrations (i.e. mean accuracies between 90% and 110%). The formulations of Group 2 and Group 4 were homogeneous (i.e. coefficient of variation ≤ 10%).
- Duration of treatment / exposure:
- The test item and vehicle were administered to the appropriate animals by once daily oral gavage 7 days a week for a minimum of 28 days. Main males and Recovery males were treated for 29 days, up to and including the day before scheduled necropsy. This included a minimum of two weeks prior to mating and during the mating period. For both Main and Recovery males treatment ended one day before scheduled necropsy of Main males. Main females that delivered were treated for 50-56 days, i.e. 14 days prior to mating (with the objective to cover at least two complete estrous cycles), the variable time to conception, the duration of pregnancy and at least 14 days after delivery, up to and including the day before scheduled necropsy. Recovery females were treated during the same period as Main females, until at least the first scheduled necropsy of Main females. Females which failed to deliver or had a total litter loss were treated for 42 days.
- Frequency of treatment:
- daily
Doses / concentrationsopen allclose all
- Dose / conc.:
- 100 mg/kg bw/day (actual dose received)
- Dose / conc.:
- 300 mg/kg bw/day (actual dose received)
- Dose / conc.:
- 1 000 mg/kg bw/day (actual dose received)
- No. of animals per sex per dose:
- 10 plus additional 5 in control and high dose for recovery investigations
- Control animals:
- yes, concurrent vehicle
- Details on study design:
- - Dose selection rationale: The dose levels were selected based on the results of a 14-day oral range finding study in the rat. The high dose level was the limit dose according to the guidelines. The other dose levels were chosen to provide an appropriate spacing.
- Post-exposure recovery period in satellite groups: 14 days
Examinations
- Observations and examinations performed and frequency:
- CAGE SIDE OBSERVATIONS: Yes
Throughout the study, animals were observed for general health/mortality and moribundity twice daily, in the morning and at the end of the working day. Animals were not removed from cage during observation, unless necessary for identification or confirmation of possible findings.
DETAILED CLINICAL OBSERVATIONS: Yes
Clinical observations were performed once daily, beginning during the first administration of the test item and lasting throughout the dosing and recovery period. During the dosing period, these observations were performed after dosing (no peak effect of occurrence of clinical signs was observed in the dose range finder). The time of onset, grade and duration of any observed sign was recorded. Signs were graded for severity and the maximum grade was predefined at 3 or 4. Grades were coded as slight (grade 1), moderate (grade 2), severe (grade 3) and very severe (grade 4). For certain signs, only its presence (grade 1) or absence (grade 0) was scored. In the data tables, the scored grades were reported, as well as the percentage of animals affected in summary tables.
BODY WEIGHT: Yes
Animals were weighed individually on the first day of treatment (prior to dosing), and weekly thereafter. Mated Main females were weighed on Days 0, 4, 7, 11, 14, 17, and 20 post-coitum and during lactation on PND 1, 4, 7, and 13. A fasted weight was recorded on the day of necropsy.
FOOD CONSUMPTION: Yes
Food consumption was quantitatively measured weekly, except for Main males and Main females which were housed together for mating and for Main females without evidence of mating. Food consumption of mated Main females was measured on Days 0, 4, 7, 11, 14, 17, and 20 post-coitum and during lactation on PND 1, 4, 7, and 13.
WATER CONSUMPTION: Yes
Subjective appraisal was maintained during the study, but no quantitative investigation was introduced as no effect was suspected.
OPHTHALMOSCOPIC EXAMINATION: No
HAEMATOLOGY: Yes
- Time schedule for collection of blood: on the day of scheduled necropsy
- Anaesthetic used for blood collection: Yes (isoflurane)
- Animals fasted: Yes
- How many animals: 5/sex of main animals and all recovery animals
- Parameters examined: White blood cells (WBC), Neutrophil (absolute), Lymphocyte (absolute), Monocyte (absolute), Eosinophil (absolute), Basophil (absolute), Red blood cells, Reticulocyte (absolute), Red Blood Cell Distribution Width (RDW), Haemoglobin, Haematocrit, Mean corpuscular volume (MCV), Mean corpuscular haemoglobin (MCH), Mean corpuscular haemoglobin concentration (MCHC), Platelet, Prothrombin Time (PT), Activated Partial Thromboplastin Time (APTT)
CLINICAL CHEMISTRY: Yes
- Time schedule for collection of blood: on the day of scheduled necropsy
- Animals fasted: Yes
- How many animals: 5/sex of main animals and all recovery animals
- Parameters examined: Alanine aminotransferase (ALAT), Aspartate aminotransferase (ASAT), Alkaline Phosphatase (ALP), Gamma glutamyl transpeptidase (GGT), Total protein, Albumin, Total Bilirubin, Bile Acids, Urea, Creatinine, Glucose, Cholesterol, Sodium, Potassium, Chloride, Calcium, Inorganic Phosphate (Inorg. Phos),
URINALYSIS: No
NEUROBEHAVIOURAL EXAMINATION: Yes
Functional tests were performed on the selected 5 Main males and all Recovery males during Week 4 of treatment and the selected 5 Main females during the last week of lactation (i.e. on PND 9, 11 or 12), and all Recovery females were tested on the first day a Main female was tested. These tests were performed after dosing, after completion of clinical observations (including arena observation, if applicable). The following tests were performed (abbreviations mentioned in the respective tables are indicated between brackets):
• Hearing ability (HEARING) (Score 0 = normal/present, score 1 = abnormal/absent).
• Pupillary reflex (PUPIL L/R) (Score 0 = normal/present, score 1 = abnormal/absent).
• Static righting reflex (STATIC R) (Score 0 = normal/present, score 1 = abnormal/absent).
• Fore- and hind-limb grip strength, recorded as the mean of three measurements per animal (Series M4-10, Mark-10 Corporation, J.J. Bos, Gouda, The Netherlands).
• Locomotor activity (recording period: 1-hour under normal laboratory light conditions, using a computerized monitoring system, Kinder Scientific LLC, Poway, USA). Total movements and ambulations were reported. Ambulations represent movements characterized by a relocation of the entire body position like walking, whereas total movements represent all movements made by the animals, including ambulations but also smaller or more fine movements like grooming, weaving or movements of the head.
IMMUNOLOGY: No
THOYROID HORMONE MEASUREMENTS: Yes
Blood samples were processed for serum, and serum was analyzed for Thyroxine (T4). Measurement of T4 was conducted for F0-males and PND 13-15 pups. For the F0-generation, assessment of T4 (females) and Thyroid Stimulating Hormone (TSH; both sexes) was considered not relevant because no treatment-related changes in T4 were noted in F0-males, no adverse effects on thyroid histopathology and no treatment related changes in thyroid weight were recorded. Assessment of T4 for PND 4 pups and TSH for PND 13-15 pups was considered not relevant because no treatment-related changes in T4 were noted in pups at PND 13-15. - Sacrifice and pathology:
- GROSS PATHOLOGY
All animals (both Main and Recovery) were subjected to a full post mortem examination, with special attention being paid to the reproductive organs.
Animals surviving until scheduled euthanasia were weighed, and deeply anaesthetized using isoflurane and subsequently exsanguinated and subjected to a full post mortem examination. Scheduled necropsies were conducted on the following days:
- Main Males (which sired or failed to sire): Following completion of the mating period (a minimum of 28 days of administration).
- Recovery males: After the recovery period of at least 14 days, which is at least 14 days after the scheduled necropsy of Main males.
- Main Females which delivered: PND 14-16.
- Main Females which failed to deliver but showed evidence of mating (Nos. 84, 91 and 92): Post-coitum Days 27.
- Recovery females: After the recovery period of at least 14 days, which is at least 14 days after the first scheduled necropsy of Main females.
The numbers of former implantation sites were recorded for all paired Main females. In case no macroscopically visible implantation sites were present in Main females, nongravid uteri were stained using the Salewski technique in order to detect any former implantation sites and the number of corpora lutea was recorded in addition.
ORGAN WEIGHTS
The organs identified in the table below were weighed at necropsy for all scheduled euthanasia animals. Paired organs were weighed together. In the event of gross abnormalities, in addition to the combined weight, the weight of each organ of a pair was determined. Organ to body weight ratio (using the terminal body weight) were calculated.
HISTOLOGY
Representative samples of the tissues identified in table 3 below were collected from all animals and preserved in 10% neutral buffered formalin (neutral phosphate buffered 4% formaldehyde solution, Klinipath, Duiven, The Netherlands), unless otherwise indicated. The following tissues were embedded in paraffin, sectioned, mounted on glass slides, and stained with hematoxylin and eosin:
- Selected Parental animals and all Recovery animals: Tissues identified in Table 3 (except animal identification, aorta, nasopharynx, esophagus, harderian gland, lacrimal gland, salivary gland, female mammary gland, larynx, optic nerve, pancreas, skin and tongue.
- Males that failed to sire (except for males which were selected) and females that failed to delivery pups: Cervix, epididymis, coagulation gland, prostate gland, seminal vesicles, ovaries, testes, uterus and vagina.
- Remaining animals: Gross lesions/masses.
HISTOPATHOLOGY
Reproductive organs (cervix, coagulation gland, epididymides, ovaries, prostate gland, seminal vesicles, testes, uterus, and vagina):
- All Main animals of the control and high dose group.
- All males that failed to sire to examine staging of spermatogenesis and histopathology of interstitial cell structure.
- All females that failed to deliver pups.
For ovaries, a qualitative evaluation of 1 section from each ovary was made.
For testes, a detailed qualitative examination was made, taking into account the tubular stages of the spermatogenic cycle. The examination was conducted in order to identify treatment related effects such as missing germ cell layers or types, retained spermatids, multinucleate or apoptotic germ cells and sloughing of spermatogenic cells into the lumen. Any cell- or stage- specificity of testicular findings were noted.
Remaining organs:
- First five males and lactating females of the control and high dose group.
- Gross lesions for all Main and Recovery animals.
Histopathological evaluation was performed by a board-certified toxicological pathologist with training and experience in laboratory animal pathology. - Other examinations:
- For reproduction parameters see IUCLID chapter 7.8.1
- Statistics:
- All statistical tests were conducted at the 5% significance level. All pairwise comparisons were conducted using two sided tests and were reported at the 1% and 5% levels. Numerical data collected on scheduled occasions for the listed variables were analyzed as indicated according to sex and occasion. Descriptive statistics number, mean and standard deviation (or %CV or SE when deemed appropriate) were reported whenever possible. Inferential statistics were performed according to the matrix below when possible, but excluded semi-quantitative data, and any group with less than 2 observations.
The following pairwise comparisons were made:
Group 2 vs. Group 1
Group 3 vs. Group 1
Group 4 vs. Group 1
Datasets with at least 3 groups (the designated control group and 2 other groups) were compared using Dunnett-test (many-to-one-t-test). Datasets with at least 3 groups was compared using a Steel-test (many-to-one rank test). The motor activity data set was compared using an overall Kruskal-Wallis. An overall Fisher’s exact test was used to compare all groups at the 5% significance level. The above pairwise comparisons were conducted using Fisher’s exact test whenever the overall test is significant.
Results and discussion
Results of examinations
- Clinical signs:
- effects observed, non-treatment-related
- Description (incidence and severity):
- No treatment-related clinical signs were noted during daily detailed clinical observations or during weekly arena observations.
Salivation seen after dosing among animals of all dose groups, including controls, was not considered toxicologically relevant, taking into account the nature and minor severity of the effect, the absence of a dose-relationship and its time of occurrence (i.e. after dosing). Incidental findings that were noted occurred within the range of background findings to be expected for rats of this age and strain which are housed and treated under the conditions in this study. At the incidence observed, these were not considered to be signs of toxicological relevance. - Mortality:
- no mortality observed
- Description (incidence):
- No mortality occurred during the study period.
- Body weight and weight changes:
- effects observed, non-treatment-related
- Description (incidence and severity):
- Body weights and body weight gain were not considered to have been affected by treatment. The statistically significantly higher body weight and/or body weight gain of non-mated recovery females at 1000 mg/kg bw/day on a few days during the treatment period were considered to be unrelated to treatment, as the differences were small and since body weight of high dose pregnant females was not affected. This variation was ascribed to the lower number of females after Day 1 of the Repro period (n=5) compared to Day 1 (n=15), whereby the slightly higher mean body weight of Group 4 recovery females compared to controls was considered to have occurred by chance.
- Food consumption and compound intake (if feeding study):
- effects observed, non-treatment-related
- Description (incidence and severity):
- Food consumption before or after correction for body weight was not considered to have been affected by treatment. Any statistically significant changes in food consumption before or after correction for body weight were considered to be unrelated to treatment since no trend was apparent regarding dose and/or duration of treatment.
- Food efficiency:
- not examined
- Water consumption and compound intake (if drinking water study):
- no effects observed
- Ophthalmological findings:
- not examined
- Haematological findings:
- effects observed, non-treatment-related
- Description (incidence and severity):
- Haematological parameters of treated rats were considered not to have been affected by treatment. Any statistically significant alterations in hematological parameters (higher reticulocyte counts in males of the recovery period, lower erythrocyte counts in main group females at 100 mg/kg bw/day, lower neutrophil counts and MCHC values in females at the end of the recovery period) were not considered to be related to administration of the test item due to the minimal magnitude of the change, absence of a dose response, and/or absence of similar variations at the end of treatment. Coagulation parameters of treated rats were not considered to have been affected by treatment. The statistically significant higher prothrombin time (PT) in Recovery females at 1000 mg/kg bw/day at the end of treatment was not considered to be related to treatment as this finding was not noted in males and Main females at the end of treatment and since the mean remained within the range considered normal for rats of this age and strain.
- Clinical biochemistry findings:
- effects observed, non-treatment-related
- Description (incidence and severity):
- Clinical biochemistry parameters of treated rats were not considered to have been affected by treatment. The statistically significantly higher urea values for Main group males at 1000 mg/kg bw/day at the end of treatment (and a similar but statistically non-significant change in this parameter in males at 300 mg/kg bw/day) was not considered to be related to treatment. Means remained within the range considered normal for rats of this age and strain and control mean was considered to be slightly low based on this range2, and there was no clear dose-related trend. While few other changes in clinical biochemistry parameters were statistically significant (higher glucose values in main group males at 100 mg/kg bw/day, higher calcium and lower phosphate values in main group males at 300 mg/kg bw/day, lower protein and albumin values in main group females, higher chloride and potassium levels in females at the end of the recovery period), the alterations in these clinical biochemistry parameters were considered unrelated to administration of the test item due to the minimal magnitude of the change, absence of a dose response, absence of similar changes at the end of treatment and/or absence of correlating histological findings.
- Urinalysis findings:
- not examined
- Behaviour (functional findings):
- effects observed, non-treatment-related
- Description (incidence and severity):
- Functional observation parameters were not considered to be affected by treatment. Hearing ability, pupillary reflex and static righting reflex were normal in all examined animals. Motor activity was similar between treated and control groups. All groups showed a similar motor activity habituation profile with a decreasing trend in activity over the duration of the test period.
A slightly lower hind-limb grip strength (not statistically significantly) was noted for the Main and Recovery females at 1000 mg/kg bw/day at the end of treatment. Mean hind-limb strength at 1000 mg/kg bw/day remained within the range considered normal for rats of this age and strain. Also, there was no apparent trend towards a decrease based on individual values across the dose groups. Therefore, these variations were not considered to represent an effect of treatment. - Immunological findings:
- not examined
- Organ weight findings including organ / body weight ratios:
- effects observed, non-treatment-related
- Description (incidence and severity):
- There were no test item-related alterations in organ weights. Statistically significant changes differences in organ weights and/or organ to body weight ratios arising between treated and control animals (higher absolute and relative adrenal and relative kidney weights in main group males at 100 mg/kg bw/day, lower prostate weights in main group males at 300 mg/kg bw/day, lower seminal vesicle weights in males at the end of the recovery period, higher ovary weights in main group females at 300 mg/kg bw/day) were considered to have arisen by chance and not to be a sign of toxicity, in the absence of a dose-related response, correlating morphological findings and/or similar changes at the end of treatment.
- Gross pathological findings:
- effects observed, non-treatment-related
- Description (incidence and severity):
- There were no test item-related gross observations. All of the recorded macroscopic findings were within the range of background gross observations encountered in rats of this age and strain.
- Neuropathological findings:
- not examined
- Histopathological findings: non-neoplastic:
- effects observed, non-treatment-related
- Description (incidence and severity):
- There were no test item-related microscopic observations. At 100 mg/kg bw/day, one male (no. 22) showed a marked abscess of the muscular wall of the stomach with central foreign material (hair) and a female (no. 68) showed at necropsy a constriction of one uterine horn (the microscopic correlate was dilation of the horn and vacuolation of the epithelium). At 1000 mg/kg bw/day, a transitional cell papilloma of the urinary bladder of one female (no. 95) was noted. This benign neoplasm with exophytic growth pattern of fibrovascular stalks lined by regular transitional epithelium, occurred at a single incidence and was not accompanied by other urinary bladder changes in any other animal and can occasionally be observed in control rats. All of the above findings were regarded as unrelated to treatment with the test-item. The remainder of the recorded microscopic findings were within the range of background pathology encountered in rats of this age and strain. There was no test item-related alteration in the prevalence, severity, or histologic character of those incidental tissue alterations.
- Histopathological findings: neoplastic:
- not examined
- Other effects:
- no effects observed
- Description (incidence and severity):
- No effects on T4 levels in Main males.
Effect levels
- Dose descriptor:
- NOAEL
- Effect level:
- 1 000 mg/kg bw/day (actual dose received)
- Based on:
- test mat.
- Sex:
- male/female
- Basis for effect level:
- other: no adverse effects observed
Target system / organ toxicity
- Critical effects observed:
- no
Applicant's summary and conclusion
- Conclusions:
- In conclusion, based on the results of this combined 28-day repeated dose toxicity study with the reproduction/developmental toxicity screening test with a 14-day recovery period, the following no-observed-adverse-effect level (NOAEL) was established: at least 1000 mg/kg bw/day.
- Executive summary:
The objectives of this study were to determine the potential toxic effects of the test item when given orally by gavage for a minimum of 28 days to Wistar Han rats, followed by a 14-day recovery period and to evaluate the potential to affect male and female reproductive performance such as gonadal function, mating behaviour, conception, parturition and early postnatal development. The recovery animals (used to study the potential reversibility of possible toxic effects) were not mated and consequently were not used for the assessment of reproduction/ developmental toxicity. In addition, parental, reproduction (up to and including implantation) and developmental (from implantation onwards) No Observed Adverse Effect Levels (NOAELs) were evaluated. The dose levels in this study were selected to be 0, 100, 300 and 1000 mg/kg bw/day, based on the results of the dose range finder. Ten animals per sex and dose were used, additional five animals per sex were used in control and high dose groups for the recovery examinations.
Chemical analyses of formulations were conducted once during the study to assess accuracy and homogeneity. The following parameters and end points were evaluated in this study: mortality/ moribundity, clinical signs, functional observations (for 5 selected animals/sex/group and all Recovery group animals at the end of treatment), body weight and food consumption, estrous cycle determination, clinical pathology (for 5 selected animals/sex/group and all Recovery group animals at the end of treatment and end of recovery), measurement of thyroid hormone T4 (F0-males), gross necropsy findings, organ weights and histopathologic examinations. In addition, the following reproduction/developmental parameters were determined: mating and fertility indices, precoital time, number of implantation sites, gestation index and duration, parturition, maternal care, sex ratio and early postnatal pup development (mortality, clinical signs, body weights, sex, anogenital distance, areola/nipple retention and macroscopy, measurement of thyroid hormone T4 (PND 13-15 pups)). Formulation analyses confirmed that formulations of test item in corn oil were prepared accurately and homogenously. No parental toxicity was observed up to 1000 mg/kg bw/day. No reproductive toxicity was observed up to 1000 mg/kg bw/day. No developmental toxicity was observed up to 1000 mg/kg bw/day. In conclusion, based on the results of this combined 28-day repeated dose toxicity study with
the reproduction/developmental toxicity screening test with a 14-day recovery period, the following no-observed-adverse-effect levels were established for the test item:
Parental NOAEL: at least 1000 mg/kg bw/day
Reproduction NOAEL: at least 1000 mg/kg bw/day
Developmental NOAEL: at least 1000 mg/kg bw/day
Information on Registered Substances comes from registration dossiers which have been assigned a registration number. The assignment of a registration number does however not guarantee that the information in the dossier is correct or that the dossier is compliant with Regulation (EC) No 1907/2006 (the REACH Regulation). This information has not been reviewed or verified by the Agency or any other authority. The content is subject to change without prior notice.
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