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Diss Factsheets
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EC number: 215-133-1 | CAS number: 1304-56-9
- 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
Respiratory sensitisation
Administrative data
- Endpoint:
- respiratory sensitisation: in vivo
- Type of information:
- experimental study
- Adequacy of study:
- other information
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- other: Study is part of a larger program on BeO toxicity. The methods seem well established and solid. The number of animals in the study is a good base for statistical analysis.
Data source
Reference
- Reference Type:
- publication
- Title:
- Unnamed
- Year:
- 1 992
Materials and methods
- Principles of method if other than guideline:
- Inhalation study of dogs to BeO 2 years after first exposure to BeO followed by analysis of immune response of peripheral blood and lung lymphocytes.
- GLP compliance:
- no
Test material
- Reference substance name:
- Automatically generated during migration to IUCLID 6, no data available
- IUPAC Name:
- Automatically generated during migration to IUCLID 6, no data available
- Details on test material:
- No data included in this study. It is referred to a previous study by the same group.
Constituent 1
Test animals
- Species:
- dog
- Strain:
- Beagle
- Sex:
- male/female
- Details on test animals or test system and environmental conditions:
- The dogs used in the study had previously been exposed to BeO by inhalation. Dogs weighed 6.2-12.2 kg and were 44-85 months old before the initial exposure.
The animals were maintaned in indoor-outdoor kennel runs and observed twice daily. They were given 350 g of food daily and water ad libitum.
Test system
- Route of induction exposure:
- inhalation
- Remarks:
- nasal
- Route of challenge exposure:
- inhalation
- Remarks:
- nasal
- Vehicle:
- unchanged (no vehicle)
- Concentration:
- Animals were exposed pernasally to BeO (aerosol) to give a final lung burden of 50 μg/kg bw
- No. of animals per dose:
- 16 dogs
- Details on study design:
- Animals were exposed to BeO by inhalation 2.5 years after a similar exposure. Clearance of BeO from lung, immunological assays, and histopathology/cytology were assessed.
The immune response was assessed at 0, 14, 30, 60, 90, 120, 150, 165, 180 and 210 days after exposure.
Results and discussion
- Results:
- Clearance of BeO:
BeO not found in lung or excreted was generally found in the skeleton. Clearance was similar to what was previously observed
Cytologic response:
The total number of cells in lavage fluid was increased in dogs receiving the second inhalation of BeO. This response was highest 60 days after exposure and then declined. The increase was primarily due to increase in lymphocytes. Neutrophil number was also significantly increased.
Immunological response:
Proliferation of blood lymphocytes and cells isolated from lavage fluid was increased in BeO exposed animals.
Pathology:
Microgranulomas and patchy granulomatous pneumonia accompanied by focal septal fibrosis around terminal bronchioles were observed. Fibrosis into the parencyma was also observed. Macrophages with BeO was often observed in the fibrotic areas. This effect was not dependent on prior exposure to BeO.
Applicant's summary and conclusion
- Interpretation of results:
- no data
- Conclusions:
- Effects on lung do not seem to be cumulative if enough time has been between exposures.
- Executive summary:
Beagle dogs were subject to a repeat exposure of BeO 2.5 years after the first exposure. The dogs were exposed to BeO by inhalation to give a final lung burden of 50 μg/kg bodyweight. The immune response of peripheral blood and lymphocytes harvested by lung lavage was measured. Histologic examination of lung tissue, clearance of BeO from lung, and cytological response was assessed in exposed animals.
The effects on lung tissue was as previously observed with formation of infiltrates of lymphocytes and macrophages that progressed to formation of granulomas. Clearance of BeO was not significantly affected by prior exposure and similar to the results from the first exposure. Finally, there was a relatively weak effect on proliferation of lymphocytes from blood and lavage fluid.
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