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EC number: 931-227-1 | CAS number: 28497-59-8
- 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:
- sub-chronic toxicity: oral
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- other: Guideline study, GLP, japanese study
Data source
Reference
- Reference Type:
- publication
- Title:
- Unnamed
- Year:
- 1 996
Materials and methods
Test guideline
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 422 (Combined Repeated Dose Toxicity Study with the Reproduction / Developmental Toxicity Screening Test)
- Deviations:
- yes
- Remarks:
- Early version of guidance for OECD 422 not containing functional observation battery test
- GLP compliance:
- yes
- Limit test:
- no
Test material
- Reference substance name:
- Methacrylic acid, monoester with propane-1,2-diol
- EC Number:
- 248-666-3
- EC Name:
- Methacrylic acid, monoester with propane-1,2-diol
- Cas Number:
- 27813-02-1
- Molecular formula:
- C7H12O3
- IUPAC Name:
- methacrylic acid, monoester with propane-1,2-diol
- Details on test material:
- - Name of test material (as cited in study report): 2-Hydroxypropyl methacrylate
Purity: 98 %
CAS: 923-26-2
Constituent 1
Test animals
- Species:
- rat
- Strain:
- Crj: CD(SD)
- Sex:
- male/female
- Details on test animals or test system and environmental conditions:
- TEST ANIMALS
- Source: Charles River Japan
- Age at study initiation: 8 weeks
- Weight at study initiation: male 315 ~ 359 g; females 210 ~ 243 g,
- Fasting period before study: yes
- Housing: During the quarantine: suspended using a stainless steel cage type 1 with 5 per cage; Breeding: divided into separate rearing cages. Moved to a separate plastic cage, having had a natural birth .
- Diet (e.g. ad libitum): ad libitum
- Water (e.g. ad libitum): ad libitum
- Acclimation period: five-day quarantine period and then set up a six-day acclimation period
ENVIRONMENTAL CONDITIONS
- Temperature (°C): 20-24 deg C
- Humidity (%): 40-70%
- Air changes (per hr): 12
- Photoperiod (hrs dark / hrs light): 12 hour light / 12 hour dark
Administration / exposure
- Route of administration:
- oral: gavage
- Vehicle:
- water
- Details on oral exposure:
- PREPARATION OF DOSING SOLUTIONS:
Concentration of samples was prepared by dissolving the required water for injection. The concentrations of preparation is protectedc from light at room temperature for 7 days to ensure that there were no stability issues. Preparation of 0.6% solution concentration is below the threshold level of determination, because we could not confirm the stability during the preparation for the 6% solution diluted with water for injection prepared in concentration.
VEHICLE
- Justification for use and choice of vehicle (if other than water): water
- Concentration in vehicle: 0.6, 0.8, 2.6 and 20%
- Amount of vehicle (if gavage): 5 ml/kg - Analytical verification of doses or concentrations:
- yes
- Details on analytical verification of doses or concentrations:
- No data
- Duration of treatment / exposure:
- Males :49 days
Females: from 14 days before mating to day 3 of lactation - Frequency of treatment:
- daily
Doses / concentrations
- Remarks:
- Doses / Concentrations:
0 (vehicle), 30, 100, 300 and 1000 mg/kg/ day
Basis:
nominal in water
- No. of animals per sex per dose:
- 12
- Control animals:
- yes, concurrent vehicle
- Details on study design:
- - Dose selection rationale: 2-week preliminary study
- Rationale for animal assignment (if not random): random by weight
- Terminal kill: Males, day 50; Females, day 4 of lactation - Positive control:
- not applicable
Examinations
- Observations and examinations performed and frequency:
- CAGE SIDE OBSERVATIONS: Yes
- Time schedule: twice a day
- Cage side observations: general condition
DETAILED CLINICAL OBSERVATIONS: Yes / No / No data
- Time schedule:
BODY WEIGHT: Yes
- Time schedule for examinations: twice a week
FOOD CONSUMPTION AND COMPOUND INTAKE (if feeding study): 2 times per week
- Food consumption for each animal determined and mean daily diet consumption calculated as g food/kg body weight/day: No data
- Compound intake calculated as time-weighted averages from the consumption and body weight gain data: No data
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 (if drinking water study): No
OPHTHALMOSCOPIC EXAMINATION: No
HAEMATOLOGY: Yes
- Time schedule for collection of blood:day after treatment
- Anaesthetic used for blood collection: Yes (identity) : sodium pentobarbital
- Animals fasted: No data
- Parameters checked in table [No.1] were examined.
CLINICAL CHEMISTRY: Yes
- Time schedule for collection of blood: day after treatment
- Animals fasted: No data
- Parameters checked in table [No.2] were examined.
URINALYSIS: No
NEUROBEHAVIOURAL EXAMINATION: No
OTHER: sexual cycle until confirmation; status of delivery - Sacrifice and pathology:
- GROSS PATHOLOGY: Yes; Males: Thymus, liver, kidney, testis and epididymis weight was measured after removal, adrenal gland, brain, heart and spleen and 10% neutral buffered formalin solution (However, testicular and epididymal fluid Buan) was fixed; Females: counting the number of corpora lutea and the number of implantation scars. Liver, kidney, ovary and thymus weight was measured after removal, adrenal gland, brain, heart and spleen with a fixed 10% neutral buffered formalin solution.
HISTOPATHOLOGY: Yes; Control group and 1000 mg / kg group of heart, liver, spleen, thymus, kidney, testis, epididymis, ovary, adrenal and brain for the Preparation HE staining of tissue was examined histologically. - Statistics:
- In either test, significant risk factors were less than 5%.
1) multiple comparison test
Weight (the parent animals, babies), food consumption, number of estrus, days mating, pregnancy [Day delivery (feeding 0) - date confirmed mating, the number of implantation scars, the number of birth control mobilize (number of babies stillborn baby + ), the number of newborn, number of children born dead, birth rate [(number of birth control mobilize / number of implantation scars) × 100], rate of production of child [(number of infant feeding 0 days / number of implantation scars) × 100], corpus number, implantation rates [(number of implantation scars / number of corpora lutea) × 100], fertility [(number of infant feeding 0 day / mobilize all of birth control) × 100], feeding baby number four day, feeding 4 day survival rate [(number of newborn feeding 4 days / 0 Number of infant feeding day) × 100], unusual occurrence rate [(number of children with abnormal/ number of newborns) × 100], sex ratio (male / female), organ weights ( including the relative weight), results of blood tests, blood biochemistry test results for the mean and standard deviation were calculated for each group. Significant difference test, Bartlett's test and the homoscedasticity of Law, Law-way layout analysis of variance if the variance 1) and, if significant Dunnett method 2) or Scheff Method 3) were using. However, if the variance was not approved, the analysis method using centrally located position (Kruskal-Wallis test of 4)) and a significant if you use the ranking method or Dunnett Scheff Method was used.
2) χ ^ 2 test
Copulation rate [(number of established animal mating / number of live animals) × 100], fertility [(number of female fertility / Establishment of animal mating) × 100], the birth rate [(number of female newborns / number of female fertility) × 100] is, χ ^ 2 using the test.
Results and discussion
Results of examinations
- Clinical signs:
- effects observed, treatment-related
- Mortality:
- mortality observed, treatment-related
- Body weight and weight changes:
- no effects observed
- Food consumption and compound intake (if feeding study):
- no effects observed
- Food efficiency:
- not examined
- Water consumption and compound intake (if drinking water study):
- not examined
- Ophthalmological findings:
- not examined
- Haematological findings:
- effects observed, treatment-related
- Clinical biochemistry findings:
- no effects observed
- Urinalysis findings:
- not examined
- Behaviour (functional findings):
- not examined
- Organ weight findings including organ / body weight ratios:
- effects observed, treatment-related
- Gross pathological findings:
- no effects observed
- Histopathological findings: non-neoplastic:
- no effects observed
- Histopathological findings: neoplastic:
- no effects observed
- Details on results:
- For the males, salivation, decrease in locomotor activity and ptosis were found in the 1000 mg/kg group, and 2 animals of the group died. Decrease in hematocrit, tendencies for decrease in RBC and hemoglobin, and increase in the relative liver weights were also found in the 1000 mg/kg group.
For the females, salivation, decrease in locomotor activity and ptosis were found in the 1000 mg/kg group, and 1 animal died.
Effect levels
- Dose descriptor:
- NOAEL
- Effect level:
- 300 mg/kg bw/day (nominal)
- Based on:
- test mat.
- Sex:
- male/female
- Basis for effect level:
- clinical biochemistry
- clinical signs
- haematology
- mortality
- organ weights and organ / body weight ratios
Target system / organ toxicity
- Critical effects observed:
- not specified
Applicant's summary and conclusion
- Conclusions:
- In an OECD 422 study in rats, the oral repeated dose NOAEL was determined to be 300 mg/kg based on body weights.
- Executive summary:
According to the OECD test guidelines for combined repeated dose toxicity study with the reproductive/developmental toxicity screening test [OECD TG 422], SD (Crj: CD) rats (12 animals/dose/sex) were administrated with this substance by gavage at doses of 0 (vehicle; water for injection), 30, 100, 300, and 1,000 mg/kg bw/day (12 animal/dose/sex). Males were dosed for a total of 49 days beginning 14 days before mating, and females were dosed for total of 41 to 48 days starting from 14 days before mating to day 4 of lactation throughout the mating and pregnancy period.
At 1000 mg/kg bw/day for males, two of the 12 animals died. Salivation, decreases in locomotor activity, ptosis were observed. The decrease in hematocrit and the tendencies for decrease in erythrocyte (RBC) and hemoglobin were found in haematological examination. The statistically significant increase in the relative liver weights was observed in organ weight. At that for females, one of the 12 animals died. Salivation, decreases in locomotor activity, ptosis were observed. The other significant toxicological changes were not observed.
At 0, 30, 100 and 300 mg/kg bw/day for both sexes, no animals died and no abnormal clinical changes were observed. Moreover, significant toxicological changes were not observed in body and organ weight, food consumption, haematological examination, blood chemical examination, necropsy, and histopathological examination. Therefore, no adverse effect was observed in both sexes.
The NOAELs for the repeated dose toxicity are considered to be 300 mg/kg bw/day for both sexes.
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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