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EC number: 700-810-0 | CAS number: 58190-62-8
- 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
Genetic toxicity: in vivo
Administrative data
- Endpoint:
- in vivo mammalian somatic cell study: cytogenicity / erythrocyte micronucleus
- 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:
- 2 012
- Report date:
- 2012
Materials and methods
Test guidelineopen allclose all
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 474 (Mammalian Erythrocyte Micronucleus Test)
- Deviations:
- no
- Qualifier:
- according to guideline
- Guideline:
- EU Method B.12 (Mutagenicity - In Vivo Mammalian Erythrocyte Micronucleus Test)
- Deviations:
- no
- Qualifier:
- according to guideline
- Guideline:
- EPA OPPTS 870.5395 (In Vivo Mammalian Cytogenetics Tests: Erythrocyte Micronucleus Assay)
- Deviations:
- no
- Qualifier:
- according to guideline
- Guideline:
- JAPAN: Guidelines for Screening Mutagenicity Testing Of Chemicals
- Deviations:
- no
- GLP compliance:
- yes (incl. QA statement)
- Type of assay:
- micronucleus assay
Test material
- Reference substance name:
- -
- EC Number:
- 484-460-1
- EC Name:
- -
- Cas Number:
- 37859-55-5
- Molecular formula:
- C16H33N3O3Si
- IUPAC Name:
- O,O',O''-(methylsilylidyne)trioxime 2-pentanone
- Reference substance name:
- O,O',O"-(methylsilylidyne)trioxime 2-pentanone
- IUPAC Name:
- O,O',O"-(methylsilylidyne)trioxime 2-pentanone
- Details on test material:
- - Name of test material (as cited in study report): OS1600
- Molecular formula (if other than submission substance): C16H33N3O3Si
- Molecular weight (if other than submission substance): 343.55
- Smiles notation (if other than submission substance): CCCC(\C)=N\O[Si](C)(O\N=C(/C)CCC)O\N=C(\C)CCC
- InChl (if other than submission substance): Mixture of all possible stereoisomers.
- Structural formula attached as image file (if other than submission substance): see Fig.
Constituent 1
Constituent 2
Test animals
- Species:
- rat
- Strain:
- Sprague-Dawley
- Sex:
- male
- Details on test animals or test system and environmental conditions:
- All animals used on this study were Crl: CD(SD) rats and were sourced from Charles River UK Limited, Margate, Kent, England. Animals
used on the study weighed between:
Preliminary toxicity test: Males weighed between 194g to 205g.
Females weighed between 164g to 181g.
Micronucleus test: Males weighed between 174g to 224g
Animal age on despatch and on Day 1 of dosing were:
Preliminary toxicity test: On despatch Males and females ca 42 days old.
Day 1 Males and females ca 48 days old.
Micronucleus test: On despatch Males ca 42 days old.
Day 1 Males ca 49 days old.
Each group was kept, with the sexes separated, in cages and maintained in a controlled environment, with the thermostat and relative humidity target ranges set at 19 to 23°C and 40 to 70% respectively. Temperature and humidity were within range throughout the study. The room was
illuminated by artificial light for 12 hours per day. All animals were allowed free access to pelleted expanded rat and mouse No.1 maintenance
diet (SQC grade obtained from Special Diets Services Ltd, Witham, Essex, UK) and tap water ad libitum.
Food, chew blocks and tap water are routinely analysed for quality at source. All animals were given small soft white untreated wood (ASPEN) chew blocks and a red plastic shelter for environmental enrichment, were acclimatised for a minimum of 5 days, examined daily and weighed prior to dosing.
Administration / exposure
- Route of administration:
- oral: gavage
- Vehicle:
- Corn oil
- Details on exposure:
- Stability and homogeneity of the test substance and of the test substance in the vehicle were not determined in this test and remain the responsibility of the Sponsor. Chemical analysis of dosing formulations for achieved concentration was not performed in this study.
Suspensions of the test substance were prepared in Corn oil obtained from Sigma, batch number MKBF6012V and MKBG9425V.
Cyclophosphamide obtained from Sigma, batch number 120M1253V was used as the positive control compound. A solution was prepared using purified water at a concentration of 2 mg/mL just prior to administration.
All animals were dosed orally by gavage. The vehicle control and test substance groups were dosed using a dose volume of 2 mL/kg. The positive control group were dosed using a dose volume of 10 mL/kg. - Duration of treatment / exposure:
- 2 consecutive days
- Frequency of treatment:
- daily for 2 consecutive days
Doses / concentrationsopen allclose all
- Dose / conc.:
- 125 mg/kg bw/day (nominal)
- Dose / conc.:
- 250 mg/kg bw/day (nominal)
- Dose / conc.:
- 500 mg/kg bw/day (nominal)
- No. of animals per sex per dose:
- 6 males at 125 mg/kg/day
6 males at 250 mg/kg/day
8 males at 500 mg/kg/day (due to toxicity) - Control animals:
- yes, concurrent vehicle
- Positive control(s):
- Cyclophosphamide (single dose at 20 mg/kg/day, 2 mg/mL)
Examinations
- Tissues and cell types examined:
- Femur bone marrow.
- Details of tissue and slide preparation:
- The femurs were cleaned of all excess tissue and blood and the proximal epiphysis removed from each bone. The bone marrow of the femurs from each animal was flushed out and pooled in a total volume of 3 mL of filtered foetal calf serum by aspiration.
The resulting cell suspensions were centrifuged at 1000 rpm (150 x g) for 5 minutes and the supernatant discarded. The final cell pellet was resuspended in a small volume of foetal calf serum to facilitate smearing in the conventional manner on glass microscope slides (Schmid 1976).
Fixation and slide staining:
1 Fixed for a minimum of 10 minutes in methanol and allowed to air-dry
2 Rinsed in purified water
3 Stained in acridine orange solution (0.0125 mg/mL using purified water) for 4 minutes
4 Washed in purified water for 5 minutes
5 Rinsed in cold tap water for 2 minutes
6 Stored at room temperature until required
7 Immediately prior to scoring, slides are wet mounted with coverslips using purified water
Coded slides were examined by fluorescence microscopy and 2000 polychromatic erythrocytes per animal were examined for the presence of micronuclei. The proportion of polychromatic erythrocytes was assessed by examination of a total of at least 1000 erythrocytes per animal and the number of micronucleated normochromatic erythrocytes was recorded. - Evaluation criteria:
- A positive response is normally indicated by a statistically significant increase in the incidence of micronucleated polychromatic erythrocytes for the treatment group compared with the vehicle control group (p<0.01); individual and/or group mean values should exceed the laboratory historical control range (Morrison and Ashby 1995).
A negative result is indicated where individual and group mean incidences of micronucleated polychromatic erythrocytes for the group treated with the test substance are not significantly greater than incidences for the concurrent vehicle control group and where these values fall
within the historical control range.
An equivocal response is obtained when the results do not meet the criteria specified for a positive or negative response.
Bone marrow cell toxicity (or depression) is normally indicated by a substantial and statistically significant decrease in the proportion of polychromatic erythrocytes (p<0.01). - Statistics:
- For the proportion of polychromatic erythrocytes at 24 hours, an asymptotic one-tailed Jonckheere’s test for trend (Jonckheere 1954) with “step-down” was used on Groups 1 to 4 for a decrease from control. If significant, then the analysis was carried out on Groups 1 to 3, then on Groups 1 and 2. Exact one-tailed Wilcoxon pairwise tests (Wilcoxon 1945), for a decrease from control, were also carried out on Group 1 (control) versus Groups 2, 3, 4 and 5.
For micronucleated polychromatic erythrocytes at 24 hours, an exact one-tailed Linear-by-Linear association test (Cytel 1995) with “step-down” was used on Groups 1 to 4 for an increase from control. If significant, then the analysis was carried out on Groups 1 to 3. Also, exact one-tailed pairwise Permutation tests (Cytel 1995), for an increase from control, were carried out on Group 1 (control) versus Groups 2, 3, 4 and 5.
Statistical significance was declared at the 1% level for all tests.
Results and discussion
Test results
- Key result
- Sex:
- male
- Genotoxicity:
- negative
- Toxicity:
- yes
- Vehicle controls validity:
- valid
- Positive controls validity:
- valid
- Additional information on results:
- RESULTS OF RANGE-FINDING STUDY
- Dose range: 500 and 1000 mg/kg bw/day
- Animals: 2 rats per sex and per dose
- Clinical signs of toxicity in test animals:
At 500 mg/kg bw/day: unsteady gait, piloerection, underactive behaviour and hunched posture, hindlimbs (females). All animals survived until scheduled termination on Day 3. No net loss in bodyweight was observed.
At 1000 mg/kg bw/day: Unsteady gait, piloerection, underactive behaviour, splayed hindlimbs (males), prostrate posture, slow breathing, shallow breathing (males), deep breathing (males) and unresponsive behaviour (males), overactive behaviour (females), uncoordinated gait (females) and hunched posture (females). Animals were killed in extremis on Day 1, 1.5 and 2.5 hours post dose due to the severity of the clinical signs observed, consequently the maximum tolerated dose had been exceeded. The post mortem examinations did not find any signs of mis-dosing
RESULTS OF DEFINITIVE STUDY
- Micronucleated polychromatic erythrocyte counts (MPCE): No statistically significant increases in the number of MPCE in male animals. Cyclophosphamide caused a statistically significant increase in the frequency of MPCE (p<0.01) in male animals.
- Micronucleated normochromatic erythrocytes (MNCE): No significant increases in the incidence of MNCE in male animals.
- Proportion of polychromatic erythrocytes (%PCE): No statistically significant decreases in the proportion of PCE in male animals. Cyclophosphamide caused a statistically significant decrease in the proportion of PCE (p<0.01) in male animals.
- Clinical signs: At 250 mg/kg/day underactive behaviour, piloerection and unsteady gait were observed. At 500 mg/kg/day unsteady gait, underactive behaviour, piloerection, hindlimbs splayed, rales/noisy breathing and hunched posture were observed. Bodyweight loss of 15% from Day 2 to Day 3 was observed in one animal administered 500 mg/kg/day test item.
Applicant's summary and conclusion
- Conclusions:
- OS1600 was determined not to cause an increase in the induction of micronucleated polychromatic erythrocytes or bone marrow cell toxicity in male CD(SD) rats.
- Executive summary:
An in-vivo micronucleus test in Crl: CD(SD) rats was performed with the analogue substance OS1600 according to OECD Guideline 474. Based on preliminary results, 6 -8 male rats per group were treated with 0 (control), 125, 250 and 500 mg/kg bw orally by gavage (2 mL/kg) on two occasions approximately 24 hours apart. Bone marrow smears were obtained from animals in the vehicle control and in each of the test substance groups 24 hours after administration of the second dose. One smear from each animal was examined for the presence of micronuclei in 2000 polychromatic erythrocytes (MPCE). The proportion of polychromatic erythrocytes (%PCE) was assessed by examination of at least 1000 erythrocytes from each animal. A record of the incidence of micronucleated normochromatic erythrocytes (MNCE) was also kept. No statistically significant increases in the frequency of MPCE and no statistically significant decreases in the % PCE were observed at any treatment level, compared to vehicle control values. OS1600 did not show any evidence of causing an increase in the induction of MPCE or bone marrow cell toxicity in male rats when administered orally by gavage in this in vivo test procedure. Based on these results, the read-across approach was applied and the substance OS2600 was also determined to be negative in the in-vivo micronucleus test under test conditions.
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