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EC number: 231-974-7 | CAS number: 7783-00-8
- 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
- Remarks:
- Type of genotoxicity: chromosome aberration
- Type of information:
- experimental study
- Adequacy of study:
- supporting study
- Study period:
- no data available
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- other: Reliable with restrictions, as purity and identity of the test item are missing and as the experimental procedure is poorly described. Due to reporting deficiencies this reference will only be used as supportive information.
Data source
Reference
- Reference Type:
- publication
- Title:
- Micronucleus induction by chromium and selenium, and suppression by metallothionein inducer.
- Author:
- Itoh S, Shimada H.
- Year:
- 1 996
- Bibliographic source:
- Mutat. Res. 367, 233-236
Materials and methods
Test guideline
- Qualifier:
- no guideline followed
- Principles of method if other than guideline:
- The clastogenic effect of selenium compounds in mouse bone marrow cells has been investigated.
- GLP compliance:
- no
- Type of assay:
- micronucleus assay
Test material
- Reference substance name:
- Selenious acid
- EC Number:
- 231-974-7
- EC Name:
- Selenious acid
- Cas Number:
- 7783-00-8
- Molecular formula:
- H2O3Se
- IUPAC Name:
- selenous acid
- Details on test material:
- - Name of test material (as cited in study report): Selenious acid
- Molecular formula (if other than submission substance): H2SeO3
- Physical state: solid
No further details are given.
Constituent 1
Test animals
- Species:
- mouse
- Strain:
- other: Slc:ddY
- Sex:
- male
- Details on test animals or test system and environmental conditions:
- TEST ANIMALS
- Source: Japan SLC Inc. (Hamamatsu, Shizuoka)
- Age at study initiation: 8-week old
- Housing: 5 mice per metal cage
- Diet: ad libitum
- Water: ad libitum
No further details are given.
Administration / exposure
- Route of administration:
- intraperitoneal
- Vehicle:
- - Vehicle(s)/solvent(s) used:physiological saline
No further details. - Details on exposure:
- No further details are given.
- Duration of treatment / exposure:
- for 2 consecutive days
- Frequency of treatment:
- once a day
- Post exposure period:
- 24 hours
Doses / concentrationsopen allclose all
- Remarks:
- Doses / Concentrations:
0.625 mg/kg
Basis:
nominal conc.
- Remarks:
- Doses / Concentrations:
1.25 mg/kg
Basis:
nominal conc.
- Remarks:
- Doses / Concentrations:
2.5 mg/kg
Basis:
nominal conc.
- Remarks:
- Doses / Concentrations:
5 mg/kg
Basis:
nominal conc.
- No. of animals per sex per dose:
- 5 mice per treatment group
- Control animals:
- yes, concurrent vehicle
- Positive control(s):
- mitomycin C
- Doses / concentrations: 0.5 mg/kg
Examinations
- Tissues and cell types examined:
- bone marrow
- Details of tissue and slide preparation:
- CRITERIA FOR DOSE SELECTION: The dose levels were determined on the basis of preliminary dose finding tests for maximum survival dose.
TREATMENT AND SAMPLING TIMES ( in addition to information in specific fields): Animals were killed by cervical dislocation at 24 hours after the second administration and the bone marrow was flushed into a tube containing foetal bovine serum.
DETAILS OF SLIDE PREPARATION: Bone marrow smears were prepared and stained with acridine orange.
METHOD OF ANALYSIS: For each animal, 1000 polychromatic erythrocytes (PCE) were scored for micronuclei (MN) and the frequency of micronucleated polychromatic erythrocytes (MNPCE) was expressed as percent of PCE. A number of PCE in 1000 total erythrocytes (PCE plus normochromatic erythrocytes) were also recorded. - Evaluation criteria:
- no data
- Statistics:
- The Kastenbaum and Bowman method (1970) was used for statistical analysis of MNPCE.
Results and discussion
Test results
- Sex:
- male
- Genotoxicity:
- positive
- Remarks:
- H2SeO3 induced a significant increase in MN-PCE at the highest dose.
- Toxicity:
- not specified
- Vehicle controls validity:
- valid
- Negative controls validity:
- not examined
- Positive controls validity:
- valid
- Additional information on results:
- No further details are given.
Any other information on results incl. tables
Induction of MNPCE by H2SeO3
Compound | Dose (mg/kg) | MNPCE (%) | range | PCE (%) | range |
Control** | 0 | 0.14 +/- 0.05 | 0 -0.3 | 58.3 +/- 2.9 | 49.1 -77.9 |
H2SeO3 | 0.625 | 0.14 +/- 0.07 | 0 -0.3 | 61.8 +/- 2.3 | 57 -70.4 |
1.25 | 0.20 +/- 0.05 | 0.1 -0.4 | 53.7 +/- 2.7 | 45.6 -58.7 | |
2.5 | 0.30 +/- 0.08 | 0.2 -0.6 | 61.0 +/- 3.0 | 51.8 -67.6 | |
5.0 | 2.50 +/- 0.61* | 1.0 -4.1 | 45.2 +/- 3.3 | 35.8 -55.0 | |
mitomycin C | 0.5 | 2.27 +/- 0.15* | 1.0 -3.8 | 58.7 +/- 1.1 | 46.5 -65.9 |
* Significant difference from current control (p<0.01)
** Sum of 4 experiments
Applicant's summary and conclusion
- Conclusions:
- Interpretation of results (migrated information): other: Increase in micronucleated cells only at very high, nearly lethal dose, questionable biological relevance. Should only be used as supportive information.
A significant increase in micronucleated cells was observed, with a clear positive finding in the maximum dose of 5 mg/kg. All lower dose levels were in the range of the control (0.0-0.3% MNPCE). However, the dose selection was not clearly justified and a description of the toxic effects is lacking. As stated below one might speculate that the maximum dose already showed signs of near-lethal toxicity, making this positive finding of questionable biological significance.
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