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EC number: 700-041-0 | CAS number: -
- 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

Genetic toxicity: in vivo
Administrative data
- Endpoint:
- in vivo mammalian somatic cell study: cytogenicity / bone marrow chromosome aberration
- Type of information:
- read-across from supporting substance (structural analogue or surrogate)
- Adequacy of study:
- key study
- Study period:
- 2001
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- test procedure in accordance with generally accepted scientific standards and described in sufficient detail
Data source
Reference
- Reference Type:
- study report
- Title:
- Unnamed
- Year:
- 2 001
- Report date:
- 2001
Materials and methods
Test guideline
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 474 (Mammalian Erythrocyte Micronucleus Test)
- GLP compliance:
- yes (incl. QA statement)
- Type of assay:
- mammalian bone marrow chromosome aberration test
Test material
- Reference substance name:
- (2S)-2-[(4R)-2-Oxo-4-propyl-1-pyrrolidinyl]butanamide
- Cas Number:
- 357336-20-0
- Molecular formula:
- C11H20N2O2
- IUPAC Name:
- (2S)-2-[(4R)-2-Oxo-4-propyl-1-pyrrolidinyl]butanamide
- Test material form:
- solid: particulate/powder
Constituent 1
Test animals
- Species:
- rat
- Strain:
- Wistar
- Details on species / strain selection:
- HsdOla:WI
- Sex:
- male/female
Administration / exposure
- Route of administration:
- oral: gavage
- Vehicle:
- The vehicle control material used was 1% w/v aqueous methylcellulose (400 cps)
- Details on exposure:
- Because of the short half-life, the animals were doced twice a day (2 equal sub-doses given 6 h apart)
- Duration of treatment / exposure:
- 2 consecitive days
- Frequency of treatment:
- twice a day (2 equal sub-doses given 6 h apart) for 2 consecitive days
- Post exposure period:
- 48 h bone marrow sampling
Doses / concentrationsopen allclose all
- Dose / conc.:
- 500 mg/kg bw/day
- Dose / conc.:
- 1 000 mg/kg bw/day
- Dose / conc.:
- 2 000 mg/kg bw/day
- No. of animals per sex per dose:
- standard 5 males and 5 females
- Control animals:
- yes, concurrent vehicle
- Positive control(s):
- control material used was 1% w/v aqueous methylcellulose
Results and discussion
Test results
- Key result
- Sex:
- male/female
- Genotoxicity:
- negative
- Toxicity:
- no effects
- Vehicle controls validity:
- valid
Applicant's summary and conclusion
- Conclusions:
- It was concluded that ucb 34714 did not induce micronuclei in bone marrow cells when tested, in male and female Wistar rats, to the maximum tolerated oral dose of 2000 mg.kg-l day-l given as 2 equal daily sub-doses 6 h apart for 2 consecutive days.
- Executive summary:
he in vivo genotoxic potential of ucb 34714 was evaluated in a micronucleus test in bone marrow erythrocytes of young, male and female Wistar rats. The animals were dosed twice daily (2 equal sub-doses given 6 h apart) for 2 consecutive days (ie 4 consecutive doses at O, 6, 24 and 30 h). The dosing regimen was based on Sponsor information that the test material has a short half-life in rats. The rats were dosed orally by gavage.
A toxicity study was undertaken to establish a suitable dose range for the micronucleus experiment. Based on the findings of the toxicity study, the maximum tolerated dose of ucb 34714 was judged to be in the region of 2000 mg.kg-l.day-l.
In the micronucleus test, male rats were dosed with the test item at concentrations equivalent to 500, 1000 and 2000 mg.kg-l.day-l. Female rats were dosed with the test item at 2000 mg.kg-’ day-l. Bone marrow samples were taken 48 h after the initial dose. Two control groups of Wistar rats were dosed orally with either the vehicle, (1YOw/v aqueous methyl cellulose), (males and females) or the positive control agent, (50 mg cyclophosphamide. kg-i. day-l (males only). The experimental schedule for the control groups followed that of the test item treated rats. Each group consisted of 5 rats per sex where applicable. An additional 5 animals/sex were dosed with the test item at 2000 mg.kg-l day-l, and served as a contingency in case of unscheduled deaths. Blood samples for toxicokinetic analysis were taken 1.5 h after the last dose.
No micronucleus induction was detected in bone marrow erythrocytes of rats dosed with ucb 34714.
Animals treated with the vehicle alone showed normal background levels of micronuclei, while animals dosed with cyclophosphamide responded with substantial increases in the numbers of bone marrow micronuclei.
It was concluded that ucb 34714 did not induce micronuclei in bone marrow cells when tested, in male and female Wistar rats, to the maximum tolerated oral dose of 2000 mg.kg-l day-l given as 2 equal daily sub-doses 6 h apart for 2 consecutive days.
The toxicokinetic analysis indicated that the males dosed with 500, 1000 and 2000 mg.kg-l.day-l had mean plasma levels of 76.7*3.9, 98.9+30.7 and 265fl 33 pg.ml-i respectively 1.5 h after the last sub-dose. The females dosed with 2000 mg.kg-l.day-l were found to have plasma levels of 393*6 pg.ml-l 1.5 h after the last sub-dose.
This study was performed in accordance with the Principles of Good Laboratory Practice.
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