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EC number: 202-284-3 | CAS number: 93-89-0
- 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
Endpoint summary
Administrative data
Description of key information
In a Combined Repeated Oral (Dietary) Dose Toxicity Study with Reproduction/Developmental Toxicity Screening Test according to OECD guideline 422, the no observed adverse effect level (NOAEL) of the test substance was 1.6% (corresponding to 953.6 mg/kg bw/day for males and 1294.5 mg/kg bw/day for females) in general toxicity, reproductive toxicity and developmental toxicity respectively, under the conditions of this study.
Key value for chemical safety assessment
Repeated dose toxicity: via oral route - systemic effects
Link to relevant study records
- Endpoint:
- short-term repeated dose toxicity: oral
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Study period:
- 2021-08-24 to 2022-05-22
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- guideline study
- Reason / purpose for cross-reference:
- reference to same study
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 422 (Combined Repeated Dose Toxicity Study with the Reproduction / Developmental Toxicity Screening Test)
- Version / remarks:
- adopted 2016-07-29
- Deviations:
- no
- Qualifier:
- according to guideline
- Guideline:
- other: “Regulation on Test Methods for Chemical Substances” Notification No. 2020 46 , National Institute of Environmental Research , Republic of Korea
- Version / remarks:
- 2020-11-03
- Deviations:
- no
- GLP compliance:
- yes (incl. QA statement)
- Limit test:
- no
- Species:
- rat
- Strain:
- Sprague-Dawley
- Remarks:
- (Crl:CD(SD)), SPF
- Details on species / strain selection:
- Sprague-Dawley rats are extensively used in toxicity studies for such as reproductive and developmental toxicity, and are selected because of the abundance of historical control data to compare.
- Sex:
- male/female
- Details on test animals or test system and environmental conditions:
- TEST ANIMALS
- Females nulliparous and non-pregnant: Yes
- Age at study initiation: 10 weeks (P males), 12 weeks (P females)
- Weight at study initiation: 332.7 to 389.3 g (P males), 232.3 to 302.9 g (P females)
- Fasting period before study: No
- Housing: One animal/cage (during quarantine acclimation period and the dosing period), 1-3 animals/cage (during mating period) and one female + pups/cage (during lactation) in stainless wire mesh cages or in polycarbonate cages (from GD16 to necropsy day).
- Diet: Ad libitum
- Water: Ad libitum
- Acclimation period: The animals were acclimatized but the period was not specified.
ENVIRONMENTAL CONDITIONS
- Temperature (°C): 20.5-23.3
- Humidity (%): 52.6-67.7
- Air changes (per hr): 10-15
- Photoperiod (hrs dark / hrs light): 12/12
IN-LIFE DATES: From day 1 to day 50 (main study males), from day 1 to approx. day 67 (main study females), from PND 1 to PND 4 or 13 (F1 generation), From day 1 to day 64 (recovery group males and females) - Route of administration:
- oral: feed
- Details on route of administration:
- The oral route was chosen as it is a possible route of exposure.
- Vehicle:
- corn oil
- Details on oral exposure:
- PREPARATION OF DOSING SOLUTIONS: The required amount of the test substance was weighed and placed in a container. The required amount of vehicle (required amount: 10 mL of vehicle for 1 kg of powder feed containing test substance), corn oil, was added and mixed using a vortex mixer until dissolved. The required amount of powder feed except for the amount of the test substance was weighed. The required amount of the test substance formulation and a small amount of powder feed were mixed in a container . Then, the mixture was placed in a ball mill and residual powder feed was added and mixed using the ball mill for approximately 5-10 minutes to yield the desired concentration. The required amounts of corn oil and powder feed were weighed on an electronic balance and mixed using the ball mill for approximately 5-10 minutes for the control group.
DIET PREPARATION
- Rate of preparation of diet: Approx. weekly
- Mixing appropriate amounts with: Powder feed rodent chow (LabDiet ® CERTIFIED RODENT DIET 5002, powder type)
- Storage temperature of food: Under refrigeration conditions for 8 days, at room temperature (1 30°C) for 3 days.
VEHICLE
- Justification for use and choice of vehicle: Solubility properties
- Batch No: MKCN9742 - Analytical verification of doses or concentrations:
- yes
- Details on analytical verification of doses or concentrations:
- Homogeneity and stability analyses were conducted in a separate study (Study No B21450). The homogeneity and stability at room temperature (1-30°C) for 3 days and under refrigeration for 8 days for the dosing formulations comprising the dose levels of 0, 0.5 and 1.6% were confirmed.
Analyses of the dosing formulations were conducted in a separate study (Study No B21450). Samples were taken three times from the middle layer of each dosing formulation and analyzed for verification of dose concentration prior to dosing. As a result, the accuracies at 0.4, 0.8 and 1.6% were 87.90, 95.76 and 93.63%. These results were within the acceptable range (range: ± 20% of nominal values). - Duration of treatment / exposure:
- 49 days (main study males and recovery group males and females), approx. 66 days (2 weeks prior to mating until post-partum day 13, main study females)
- Frequency of treatment:
- Continuously (feed)
- Dose / conc.:
- 1 111.7 mg/kg bw/day (actual dose received)
- Remarks:
- Recovery group females (corresponding to 1.6% in feed)
- Dose / conc.:
- 923.2 mg/kg bw/day (actual dose received)
- Remarks:
- Recovery group males (corresponding to 1.6% in feed)
- Dose / conc.:
- 953.6 mg/kg bw/day (actual dose received)
- Remarks:
- In males, corresponding to 1.6% in feed
- Dose / conc.:
- 469.6 mg/kg bw/day (actual dose received)
- Remarks:
- In males, corresponding to 0.8% in feed
- Dose / conc.:
- 245 mg/kg bw/day (actual dose received)
- Remarks:
- In males, corresponding to 0.4% in feed
- Dose / conc.:
- 1 294.5 mg/kg bw/day (actual dose received)
- Remarks:
- In females, corresponding to 1.6% in feed
- Dose / conc.:
- 615.6 mg/kg bw/day (actual dose received)
- Remarks:
- In females, corresponding to 0.8% in feed
- Dose / conc.:
- 338.7 mg/kg bw/day (actual dose received)
- Remarks:
- In females, corresponding to 0.4% in feed
- Dose / conc.:
- 0 mg/kg bw/day (actual dose received)
- Remarks:
- Vehicle (corn oil) in feed
- No. of animals per sex per dose:
- 12 animals/sex/group (main study), 6 animals/sex/group for the control and high dose group (recovery)
- Control animals:
- yes, concurrent vehicle
- Details on study design:
- - Dose selection rationale: As a result of the 2-week dose range finding study (see IUCLID section 7.5.1), no test substance related effect was observed at 1.6%. Therefore, based on the dose range finding study, 1.6% was selected as the high dose of this study. The mid and low doses were selected at 0.8 and 0.4%, respectively, by applying a geometric ratio of 2.
- Rationale for animal assignment: Selected animals were randomly assigned to achieve even distribution of mean body weight of each group.
- Fasting period before blood sampling for clinical biochemistry: Yes, overnight (approx. 18 hours) - Positive control:
- No positive control was included in the study.
- Observations and examinations performed and frequency:
- CAGE SIDE OBSERVATIONS: Yes
- Time schedule: Once daily for clinical signs and twice daily for mortality and moribundity
DETAILED CLINICAL OBSERVATIONS: Yes
- Time schedule: Once before the start of administration and once weekly thereafter
- Detailed clinical observations comprised: Skin, fur, eyes, mucous membranes, occurrence of secretion and excretion, autonomic activity (lacrimation, piloerection, pupil size, unusual respiratory pattern, etc.), gait, posture and response to handling, and the presence of clonic or tonic movements, stereotypies (excessive grooming, repetitive circling, etc.) or bizarre behavior (self mutilation, walking backwar d, etc.)
BODY WEIGHT: Yes
- Time schedule for examinations: On the day of start of dosing (Day 1, prior to dosing) once a week during the dosing and recovery periods, and on the day of necropsy.
FOOD CONSUMPTION AND COMPOUND INTAKE:
- Food consumption for each animal determined and mean daily diet consumption calculated as g food/kg body weight/day: Yes
- Compound intake calculated as time-weighted averages from the consumption and body weight gain data: Yes
FOOD EFFICIENCY:
- Body weight gain in kg/food consumption in kg per unit time X 100 calculated as time-weighted averages from the consumption and body weight gain data: No
WATER CONSUMPTION AND COMPOUND INTAKE: No
OPHTHALMOSCOPIC EXAMINATION: No
HEMATOLOGY: Yes
- Time schedule for collection of blood: In the morning prior to necropsy
- Anaesthetic used for blood collection: Yes (isoflurane)
- Animals fasted: Yes (except neonates, overnight for approx. 18 hours)
- How many animals: All surviving animals
- Parameters checked in table 2 were examined.
CLINICAL CHEMISTRY: Yes
- Time schedule for collection of blood: In the morning prior to necropsy
- Animals fasted: Yes (except neonates, overnight for approx. 18 hours)
- How many animals: All surviving animals
- Parameters checked in table 3 were examined.
PLASMA/SERUM HORMONES/LIPIDS: Yes
- Time of blood sample collection: In the morning prior to necropsy
- Animals fasted: Yes (overnight for approx. 18 hours)
- How many animals: Pups on PND 13 and for all adult males
URINALYSIS: Yes
- Time schedule for collection of urine: Urinalysis was performed on 6 males in each group in the main group and all surviving males in the recovery group a few days before necropsy.
- Metabolism cages used for collection of urine: Not specified
- Animals fasted: Yes (Fresh urine (collected urine for about 3 hours) and collected urine for about 24 hours were examined. When fresh urine was collected, feeding and dosing were not performed. However, drinking water was provided ad libitum.)
- Parameters checked in table 1 were examined
NEUROBEHAVIOURAL EXAMINATION: Yes
- Time schedule for examinations: Functional observations were conducted on six males and females per group in the main group and all surviving animals in the recovery group a few days before necropsy.
- Dose groups that were examined: Six males and females per group in the main group and all surviving animals in the recovery group
- Battery of functions tested: Sensory activity / grip strength / motor activity
IMMUNOLOGY: No - Sacrifice and pathology:
- GROSS PATHOLOGY: Yes, gross necropsy consisted of external and internal examinations including the cervical, thoracic, and abdominal viscera. Organs weighted are listed in table 5
HISTOPATHOLOGY: Yes, tissues in Table 6 were prepared for microscopic examination - Optional endpoint(s):
- Optional endpoints: Yes, reproductive toxicity endpoints (see IUCLID section 7.8.1)
- Other examinations:
- Yes, reproductive toxicity examinations (see IUCLID section 7.8.1)
- Statistics:
- Statistical analysis was performed on the data of body weight, food consumption, estrous cycle, mating period, gestation period, post implantation loss rate, live birth index , mean litter size , body weights of pups, viability index on postnatal day s 0 and 4, external examination, sex ratio, AGD index, nipple functional observations (hindlimb landing foot splay, grip strength and motor activity) activity), urine volume, hematology, clinical chemistry , thyroid hormone and organ weights using SAS program. For the main groups and dosing period, the data was analyzed utilizing Bartlett’s test for homogeneity of variance (significance level: 0.05). One way analysis of variance (ANOVA) w as employed on homogeneous data (significance level: 0.05); then, if significant, Dunnett’s test was applied for multiple comparisons (significance levels: 0.05 and 0.01, two tailed). Kruskal Wallis test was employed on heterogeneous data (significance level: 0.05); then, if significant, DSCF (Dwass Steel Critchlow Fligner) was applied for multiple comparisons (significance levels: 0.05 and 0.01, two tailed). The data of mating index, fertility index and other data associated with gestation was analyzed utilizing Fisher’s exact test (significance levels: 0.05 and 0.01). For the recovery groups, the data was analyzed utilizing Folded F test for homogeneity of variance (significance level: 0.05). Student’s t test was employed on homogeneous data or Aspin Welch t test was employed on heterogeneous data for confirming significance (significance levels: 0.05 and 0.01, two tailed).
- Clinical signs:
- effects observed, non-treatment-related
- Description (incidence and severity):
- Delayed delivery was observed in one female in the control group on gestation day 25 and dystocia with delayed delivery were observed in one female in the 0.4 and 0.8% groups on gestation day 25 (postpartum day 0), respectively.
This was not considered to be a test substance-related effect since this effect was observed in only one female in the respective group, was also observed in the control group, and showed no dose-dependence. Thus, it was considered to be incidentally. - Mortality:
- no mortality observed
- Body weight and weight changes:
- no effects observed
- Description (incidence and severity):
- Sporadical changes with statistical significance were observed in body weight gain. These changes were temporary changes not related to feed intake, and it was considered not to be test substance-related.
- Food consumption and compound intake (if feeding study):
- no effects observed
- Description (incidence and severity):
- Sporadical changes with statistical significance were not considered to be test substance-related changes since they were minior changes and not accompanied body weight changes with statistical significance.
- Food efficiency:
- not examined
- Water consumption and compound intake (if drinking water study):
- not examined
- Ophthalmological findings:
- not examined
- Haematological findings:
- no effects observed
- Clinical biochemistry findings:
- no effects observed
- Description (incidence and severity):
- All differences in clinical chemistry parameters were of small magnitude and even if statistically significant they were considered to represent normal biological variations. In addition, the variations were neither observed in both sexes nor confirmed in related parameters. Furthermore, some changes were observed in the recovery group only.
- Endocrine findings:
- no effects observed
- Description (incidence and severity):
- Sporadical statistical differences in thyroid hormone were considered to be of no toxicological significance because they were not dose-dependent, of small magnitude or not accompanied by any morphological changes of the organ.
- Urinalysis findings:
- no effects observed
- Behaviour (functional findings):
- no effects observed
- Immunological findings:
- not examined
- Organ weight findings including organ / body weight ratios:
- no effects observed
- Description (incidence and severity):
- Sporadical statistical differences in organ weights were considered to be of no toxicological significance because they were not dose-dependent, of small magnitude or unaccompanied any morphological changes of the organ.
- Gross pathological findings:
- effects observed, non-treatment-related
- Description (incidence and severity):
- Reduction in size was observed in the testis of one male of the control group in the main group.
Dilatation of uterus and vagina was also noted in one female of the control group in the main group.
Yellowish and serous fluid in the uterus was observed in one non-copulated female of the 0.8% group in the main group.
Other macroscopic findings seen in various tissues and/or organs of all animals did not show significant differences in incidence compared to controls or were normal background lesions observed at this facility or were found with low/isolated frequency. - Neuropathological findings:
- not examined
- Histopathological findings: non-neoplastic:
- effects observed, non-treatment-related
- Description (incidence and severity):
- Minimal acute myometrial inflammation and severe dilatation in the uterus of one non-copulated female of the 0.8% dose group was observed, and the microscopic lesions corresponded to the macroscopic lesion in the uterus.
In the ovary, follicular cyst was observed in the ovary of each one of the two non-copulated female of the control and 1.6% dose groups, in the main group.
The lesions in the reproductive systems are not associated with the test substance, as they did not show significant differences in incidence between the control and 1.6% dose groups.
All other microscopic findings seen in various tissues and/or organs of all animals did not show significant differences in incidence compared to controls or were normal background lesions observed at the facility or were found with low/isolated frequency. - Histopathological findings: neoplastic:
- no effects observed
- Other effects:
- no effects observed
- Key result
- Dose descriptor:
- NOAEL
- Effect level:
- >= 953.6 mg/kg bw/day (actual dose received)
- Based on:
- test mat.
- Sex:
- male
- Remarks on result:
- not determinable due to absence of adverse toxic effects
- Key result
- Dose descriptor:
- NOAEL
- Effect level:
- >= 1 294.5 mg/kg bw/day (actual dose received)
- Based on:
- test mat.
- Sex:
- female
- Remarks on result:
- not determinable due to absence of adverse toxic effects
- Key result
- Critical effects observed:
- no
- Conclusions:
- In a Combined Repeated Oral (Dietary) Dose Toxicity Study with Reproduction/Developmental Toxicity Screening Test according to OECD guideline 422, the no observed adverse effect level (NOAEL) of the test substance was 1.6% (corresponding to 953.6 mg/kg bw/day for males and 1294.5 mg/kg bw/day for females) in general toxicity, reproductive toxicity and developmental toxicity respectively, under the conditions of this study.
- Executive summary:
The purpose of this study according to OECD guideline 422 and GLP was to determine the No Observed Adverse Effect Level (NOAEL) of the test substance for both general systemic and reproductive/developmental toxicity including gonadal function, mating behavior, conception, development of the conceptus, parturition and early postnatal development as well as the neurotoxic potential of the test substance following repeated oral administration. In addition, some endocrine disruptor relevant endpoints were evaluated. A total of 4 groups were designated as follows:
Three groups were designated as Groups 2, 3 and 4 were treated with the test substance at dose levels of 0.4, 0.8 and 1.6% (the main group 245.0, 469.6 and 953.6 mg/kg bw/day for males and 338.7, 615.6 and 1294.5 mg/kg bw/day for females, respectively, also recovery group at 1.6% were 923.2 mg/kg bw/day for males, and 1111.7 mg/kg bw/day for females, respectively.) along with a control group, Group 1 (receiving the standard basal powder feed with corn oil). Each group consisted of 12 males and 12 females for the main study. Six animals were added to each group for the recovery groups, control (G1) and high dose (G4) groups. Evaluated parameters included clinical signs, detailed clinical sign observations, body weight, food consumption, observation of estrous cycle, reproductive function, neonate examination, functional observations, urinalysis, hematology, clinical chemistry, thyroid hormone analysis, gross post mortem examination, organ weights and histopathological evaluations of selected tissues. During the observation period, no deaths of animals or test substance-related clinical signs were observed in the 0.4, 0.8 and 1.6% groups for both sexes. No test substance-related effects were noted in the detailed clinical sign observations, body weight, food consumption, observation of estrous cycle, reproductive function, neonate examination, functional observations, urinalysis, hematology, clinical chemistry, thyroid hormone analysis, gross post mortem examination, organ weights and histopathological findings in the 0.4, 0.8 and 1.6% groups of both sexes.
Based on the results, the no observed adverse effect level (NOAEL) of the test substance was 1.6% (corresponding to 953.6 mg/kg bw/day for males and 1294.5 mg/kg bw/day for females) in general toxicity, reproductive toxicity and developmental toxicity respectively, under the conditions of this study.
Reference
Endpoint conclusion
- Endpoint conclusion:
- no adverse effect observed
- Dose descriptor:
- NOAEL
- 953.6 mg/kg bw/day
- Study duration:
- subacute
- Species:
- rat
- Quality of whole database:
- Reliable without restrictions
Repeated dose toxicity: inhalation - systemic effects
Endpoint conclusion
- Endpoint conclusion:
- no study available
Repeated dose toxicity: inhalation - local effects
Endpoint conclusion
- Endpoint conclusion:
- no study available
Repeated dose toxicity: dermal - systemic effects
Endpoint conclusion
- Endpoint conclusion:
- no study available
Repeated dose toxicity: dermal - local effects
Endpoint conclusion
- Endpoint conclusion:
- no study available
Additional information
Combined Repeated Oral (Dietary) Dose Toxicity Study with Reproduction/Developmental Toxicity Screening Test, rat, RL1
The purpose of this study according to OECD guideline 422 and GLP was to determine the No Observed Adverse Effect Level (NOAEL) of the test substance for both general systemic and reproductive/developmental toxicity including gonadal function, mating behavior, conception, development of the conceptus, parturition and early postnatal development as well as the neurotoxic potential of the test substance following repeated oral administration. In addition, some endocrine disruptor relevant endpoints were evaluated. A total of 4 groups were designated as follows:
Three groups were designated as Groups 2, 3 and 4 were treated with the test substance at dose levels of 0.4, 0.8 and 1.6% (the main group 245.0, 469.6 and 953.6 mg/kg bw/day for males and 338.7, 615.6 and 1294.5 mg/kg bw/day for females, respectively, also recovery group at 1.6% were 923.2 mg/kg bw/day for males, and 1111.7 mg/kg bw/day for females, respectively.) along with a control group, Group 1 (receiving the standard basal powder feed with corn oil). Each group consisted of 12 males and 12 females for the main study. Six animals were added to each group for the recovery groups, control (G1) and high dose (G4) groups. Evaluated parameters included clinical signs, detailed clinical sign observations, body weight, food consumption, observation of estrous cycle, reproductive function, neonate examination, functional observations, urinalysis, hematology, clinical chemistry, thyroid hormone analysis, gross post mortem examination, organ weights and histopathological evaluations of selected tissues. During the observation period, no deaths of animals or test substance-related clinical signs were observed in the 0.4, 0.8 and 1.6% groups for both sexes. No test substance-related effects were noted in the detailed clinical sign observations, body weight, food consumption, observation of estrous cycle, reproductive function, neonate examination, functional observations, urinalysis, hematology, clinical chemistry, thyroid hormone analysis, gross post mortem examination, organ weights and histopathological findings in the 0.4, 0.8 and 1.6% groups of both sexes.
Based on the results, the no observed adverse effect level (NOAEL) of the test substance was 1.6% (corresponding to 953.6 mg/kg bw/day for males and 1294.5 mg/kg bw/day for females) in general toxicity, reproductive toxicity and developmental toxicity respectively, under the conditions of this study.
14-day range-finding study, rat, RL2
This study was conducted to evaluate the potential toxicity and to determine the dose levels for repeated dose study of the test substance to Sprague-Dawley rats of both sexes for 2 weeks. Test groups consisted of a dose group at a dose level of 0.4, 0.8 and 1.6 % groups and a control group (10 mL of Corn oil for 1 kg of powder feed) with 5 animals of each sex per group. All animals were dosed daily for 2 weeks by orally (dietary). During the observation period, observation of clinical signs, measurement of body weights and food consumption were performed, and after the observation period, hematology and clinical chemistry, organ weight, gross post mortem examinations were performed. No abnormal clinical signs or mortality were observed during the duration of the study. There were no test substance-related differences in food consumption, hematology, clinical chemistry, organ weights and necropsy in the animals of both sexes in the 0.4, 0.8 and 1.6% dosing groups. The mean total test substance intakes at 0.4, 0.8 and 1.6% were 288.9, 586.8 and 1150.2 mg/kg bw/day for males, and 310.0, 625.1 and 1212.6 mg/kg bw/day for females, respectively.
As a result of repeated oral (dietary) administration of the test substance to Sprague-Dawley rats of both sexes for 2-weeks, it is considered that the high dose for the long-term repeated toxicity study can be set at 1.6 % (corresponding to 1150.2 mg/kg bw/day in males and 1212.6 mg/kg bw/day in females) under the conditions of this study.
Justification for classification or non-classification
The available experimental test data are reliable and suitable for classification purposes under Regulation (EC) No 1272/2008. Based on available data on repeated dose toxicity, the test item is not classified and labelled according to Regulation (EC) No 1272/2008 (CLP), as amended for the eighteenth time in Regulation (EU) 2022/692.
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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