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EC number: 231-130-8 | CAS number: 7440-21-3
- 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 germ cell study: gene mutation
- Remarks:
- Type of genotoxicity: gene mutation
- Type of information:
- migrated information: read-across from supporting substance (structural analogue or surrogate)
- Adequacy of study:
- weight of evidence
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- other: Study well documented, meets generally accepted scientific principles, acceptable for assessment.
Cross-reference
- Reason / purpose for cross-reference:
- reference to same study
Data source
Reference
- Reference Type:
- publication
- Title:
- Pulmonary chemokine and mutagenic responses in rats after subchronic inhalation of amorphous and crystalline silica.
- Author:
- Johnston, C. J., K. E. Driscoll, et al.
- Year:
- 2 000
- Bibliographic source:
- Toxicol Sci.56(2): 405-13.
Materials and methods
Test guideline
- Qualifier:
- no guideline followed
- Principles of method if other than guideline:
- In a subchronic inhalation study, rats were exposed 6h/d, 5 d/wk to 50 mg SiO2/m3 of hydrophilic pyrogenic silica (Aerosil® 200, MMAD 0.81 µm) or cristobalite (MMAD 1.3 μm) 3 mg/m3 for up to 13 weeks. After the exposure alveolar type II cells were isolated and HPRT mutations frequency was evaluated in vitro. Apoptosis was evaluated by TUNEL staining in histological lung sections.
- GLP compliance:
- no
- Type of assay:
- other: HPRT mutations
Test material
- Reference substance name:
- amorphous silica
- IUPAC Name:
- amorphous silica
- Reference substance name:
- crystalline silica
- IUPAC Name:
- crystalline silica
- Details on test material:
- - crystalline silica: cristobalite, mass median aerodynamic diameter 1.3 μm; amorphous silica :hydrophilic pyrogenic Aerosil® 200 Degussa, mass median aerodynamic diameter 0.81 μm
Constituent 1
Constituent 2
Test animals
- Species:
- rat
- Strain:
- Fischer 344
- Sex:
- male
- Details on test animals or test system and environmental conditions:
- TEST ANIMALS
- Weight at study initiation: 200-250 g
Administration / exposure
- Route of administration:
- inhalation: dust
- Vehicle:
- no vehicle
- Details on exposure:
- TYPE OF INHALATION EXPOSURE: whole body
GENERATION OF TEST ATMOSPHERE / CHAMBER DESCRIPTION
- Exposure apparatus: Aerosols were generated by a screw-feed mechanism in combination with a venturi -type dust feeder
Controls were exposed to clean air. - Duration of treatment / exposure:
- for up to 13 weeks
- Frequency of treatment:
- 6 hours/day, 5 days/week
- Post exposure period:
- HPRT mutation frequences in alveolar type 2 cells and lung cell apoptosis were evaluated after 13 weeks of exposure
Doses / concentrations
- Remarks:
- Doses / Concentrations:
3 mg/m3 (crystalline silica); 50 mg/m3 (amorphous silica)
Basis:
- No. of animals per sex per dose:
- 4 rats/treatment
- Control animals:
- yes, sham-exposed
- Positive control(s):
- quartz
Examinations
- Tissues and cell types examined:
- alveolar type II cells
- Details of tissue and slide preparation:
- CRITERIA FOR DOSE SELECTION: exposure concentration was selected to cause significant inflammatory reaction in lungs
TREATMENT AND SAMPLING TIMES ( in addition to information in specific fields): see above
DETAILS OF SLIDE PREPARATION: after the termination of exposure, rat alveolar type II cells were isolated by standard methods and freshly isolated alveolar type II cells were seeded into culture flasks and the cells were allowed to attach overnight. The unattached cells were washed away and the cultures were fed every other day with a medium containing 6TG to select for mutation in HPRT gene. After 14-21 days in culture the cells were fixed and immunostained with an antibody to cytokeratins 8, 18, 19 and 6TG resistant cytokeratin staining colonies of >50 cells were counted.
METHOD OF ANALYSIS: Mutation frequaences were counted as (number of colonies/treatment)/(plating efficiency)/10E6 cells =mutants/10E6 cells - Statistics:
- Dunnett's test
Results and discussion
Test results
- Sex:
- male
- Genotoxicity:
- negative
- Toxicity:
- yes
- Vehicle controls validity:
- not examined
- Negative controls validity:
- valid
- Positive controls validity:
- valid
- Additional information on results:
- Endpoints studied included mutation in the hprt gene of isolated alveolar cells in an ex vivo assay, changes in bronchoalveolar lavage (BAL) fluid markers of cellular and biochemical lung injury and inflammation, expression of mRNA for the chemokine MIP-2, and detection of apoptosis (TUNEL method). After 13 weeks of exposure, the percentage of lavage neutrophils, MIP-2 expression, and lactate dehydrogenase levels as an indicator of cytotoxicity were increased in both silicas. Histopathology of the lungs showed elevated levels of neutrophils and macrophages in lungs and TUNEL staining revealed increased apoptosis. Increased hprt mutation frequency in alveolar epithelial cells was detected with crystalline silica, but not with amorphous silica .
Applicant's summary and conclusion
- Conclusions:
- Interpretation of results (migrated information): negative
Repeated inhalation exposure to synthetic amorphous silica induced lung inflammation but not genotoxicity in rat lungs whereas crystalline silica caused a positive genotoxic response. - Executive summary:
Johnston et al. (2000) conducted a 90-day subchronic inhalation toxicity study with amorphous and crystalline silica. The exposure pattern followed OECD test 413 guidance 'Subchronic inhalation toxicity: 90-day study'. The GLP status was not mentioned. Male Fischer-344 rats (200–250 g) were exposed for 6 h/day, on 5 days/wk, for up to 13 weeks to 3 mg/m3crystalline (cristobalite, mass median aerodynamic diameter 1.3 μm) or 50 mg/m3amorphous silica (hydrophilic pyrogenic Aerosil® 200 Degussa, mass median aerodynamic diameter 0.81 μm). The genotoxic effects on the lung were characterized 13 weeks of exposure. Endpoints included mutation in thehprtgene of isolated alveolar cells in anex vivoassay, changes in bronchoalveolar lavage (BAL) fluid markers of cellular and biochemical lung injury and inflammation, expression of mRNA for the chemokine MIP-2, and detection ofapoptosis. After 13 weeks of exposure, the percentage of lavage neutrophils, MIP-2 expression, and lactate dehydrogenase levels as an indicator of cytotoxicity were increased in both silicas. All parameters remained increased for crystalline silica and decreased rapidly for amorphous silica during the 8-month recovery period. Increasedhprtmutation frequency in alveolar epithelial cells was detected with crystalline silica, but not with amorphous silica. Increased TUNEL staining indicative for apoptosis was seen in macrophages and terminal bronchiolar epithelial cells mainly after exposure to amorphous silica. Lung burdens of silica were 819 and 882 μg for crystalline and amorphous silica, respectively. In summary, genotoxic effects in alveolar epithelial cells occurred only after crystalline but not amorphous silica exposure, despite a high degree of inflammatory response after subchronic exposure to both types of silica. The authors suggest that the additional factors to inflammation, such as biopersistence of particles and direct or direct cytotoxicity to target cells, are important determinants of secondary genotoxic events.
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