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EC number: 206-991-8 | CAS number: 409-21-2
- 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
Endpoint summary
Administrative data
Description of key information
In conclusion, the present investigation confirmed that SiC itself, along with SiC commercial products, has none or only a limited toxicological potential on the cellular level.
Key value for chemical safety assessment
Additional information
Available data indicate the absence of pulmonary damage after intratracheal instillation of high dose (5 mg/100 ml MRV) of SiC in rats (Vaughan et al., 1993).
Bruch et al. (1993) examined the effects of various dusts (SiC (F 1200), corundum and quartz (DQ12)) with a grain diameter < 3 µm on guinea pig alveolar macrophages (H2O2release) and CBF1-mice bone marrow macrophages (TNF-αrelease). The various dusts were studied at doses ranging from 20 to 60 µg/106cells. After 16 hours incubation, the results showed a complete inhibition of stimulation of H2O2with 60 µg Quartz, and about 40 % at the lower dose of 20 µg. By contrast, corundum and SiC had no effect on H2O2release, similar to the untreated cells. Release of TNF-αassessed by growth inhibition of L-929 cells did not differ from controls with doses of SiC up to 50 µg/well of SiC, whereas 10 µg/well of quartz led to a significant effect.
The same authors (Bruch and Rehn, 1996) then tested with comparable procedures two different SiC dusts; F 1200 (as previously) with 2.26 µm mean aerodynamic diameter and NF2 with 1.14 µm mean aerodynamic diameter. Positive control was quartz (DQ12), the negative one corundum. Cell cytotoxicity measured by lactate dehydrogenase (LDH) activity showed no significant difference in doses ranging from 20 to 180 µg/106guinea pig alveolar macrophages (AM) for two SiC or corundum dusts, whereas quartz reduced cell viability even in low doses. In contrast to the results obtained for cell viability, marked differences between the two SiC samples could be measured in the H2O2release as a measure for cell damage. Macrophages burdened with NF2 or quartz exert a significant and dose dependant reduction in H2O2release. In contrast the F 1200 samples did not show this effect, as corundum. Moreover, side-to-side comparison each fraction of sample NF2 is more toxic than sample F 1200. The authors concluded that different grain size distribution alone could not solely explain the differences. The biopathogenicity of in vitro NF2 SiC seems to consider the possible differences for the tested varieties of SiC.
Using the vector-model, a new in vitro testing concept based on the knowledge of the primary reactions of alveolar macrophages activated by the phagocytosis of dust particles, Bruch and colleagues assessed the biological activity of SiC products on the market (Bruch et al., in press). Particular attention was given to the presence of SiC cleavage fragments (CFs) in SiC commercial products. No SiC whiskers and no crystalline silica were detected in the respirable fractions from the commercial products. Average CF concentrations varied from 17 to 493 106/g of particles in the five respirable fractions of SiC grains. The in vitro doses used of 15, 30, 60 and 120 µg dust per 106AM correspond to a lung exposure of approximately 0.15 to 2,4 mg dust/rat lung via intratracheal instillation, relevant to thein vivosituation. The results showed that SiC commercial products induced a very low level of biological activity in the vector model comparable to the electrocorundum. However, in the mid and the top dose range an isolated secretion of reactive oxygen species (ROS) was observed for some samples. This increase was not related to the contents of cleavage fragments. Moreover, the isolated ROS response at higher exposure levels could not be related to in vivo toxic effects. The decrease in ROS response after heat-treatment of SiC commercial products suggested that macrophage activation is mediated by strong interactions between the surface of the particle and some cell membrane components. In conclusion, the present investigation confirmed that SiC itself, along with SiC commercial products, has none or only a limited toxicological potential on the cellular level.
Justification for classification or non-classification
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