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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
Basic toxicokinetics
Administrative data
- Endpoint:
- basic toxicokinetics in vivo
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- other: Well described study with clear aims. Experimental design and analysis seemingly sound.
Data source
Reference
- Reference Type:
- publication
- Title:
- Unnamed
- Year:
- 1 990
Materials and methods
- Objective of study:
- other: clearance, translocation and excretion
- Principles of method if other than guideline:
- Inhalation of BeO and assessment of clearance, translocation and excretion
- GLP compliance:
- no
Test material
- Reference substance name:
- Beryllium oxide
- EC Number:
- 215-133-1
- EC Name:
- Beryllium oxide
- Cas Number:
- 1304-56-9
- Molecular formula:
- BeO
- IUPAC Name:
- oxoberyllium
- Details on test material:
- Radiolabeled BeO was generated by co-precipitation of 7BeCl with BeC2O4 to form aqueous 7Be(OH)2 which was then nebulized. The aerosol stream was passed through a furnace (500C), particles collected on silver membrane filter. The particles were in turn further calcined at either 500C or 1600C for 16 hours to generate BeO.
Constituent 1
- Radiolabelling:
- yes
- Remarks:
- (7)Be
Test animals
- Species:
- dog
- Strain:
- Beagle
- Sex:
- male/female
- Details on test animals or test system and environmental conditions:
- Beagle dogs ranged in age from 20 to 61 months and from 6.2 to 12.2 kg. The animals were housed indoors with outdoor kennel runs. They were observed daily. Food was provided at 350 g per day and water was ad libitum.
Administration / exposure
- Route of administration:
- inhalation: aerosol
- Vehicle:
- unchanged (no vehicle)
- Details on exposure:
- The dogs were exposed to BeO pernasally for 5-42 minutes. The mean concentration of BeO was 28 ug/ L. The control dogs were exposed to nebulized distilled water for 30 minutes.
- Duration and frequency of treatment / exposure:
- One time exposure for 5-42 minute period.
Doses / concentrations
- Remarks:
- Doses / Concentrations:
High and low dose; BeO calcined at different temperatures (500 or 1000C) results in lung burdens of 17 and 50 ug/kg bw.
- No. of animals per sex per dose / concentration:
- n=2 for high dose, n= 7/8
- Control animals:
- yes, sham-exposed
- Details on dosing and sampling:
- Excreta was collected continously for the first 21 days followed by 3 day collections at 6, 12, 18, and 24 weeks after exposure. Radioactive whole body-count of each dog was done immediately after exposure and on day 2, 3, 4, 5, 6 and 7 followed by twice weekly for 3 months and then twice monthly.
At the end of the study, animals were sacrificed and subject to a complete necropsy. Beryllium content of tissues were determined. Histopathological examination of lungs, tracheobroncial lymph nodes was performed. - Statistics:
- Bonferroni multiple comparison test
Results and discussion
Toxicokinetic / pharmacokinetic studies
- Details on absorption:
- BeO cleared relatively slowly from the lung. BeO calcined at 500 °C cleared faster than when calcined at 1000 °C.
- Details on distribution in tissues:
- Most tissues contained levels of Be in the order of a few % of total body burden. The highest levels were found in the skeleton, tracheobroncial lymph nodes, liver, and blood.
- Details on excretion:
- Feces was the predominant route of excretion at early times and up to 6 months after exposure. Urine became predominant at later timepoints. A greater amount of the BeO calcined at 500 °C was excreted than BeO calcined at 1000 °C.
Any other information on results incl. tables
Table 1 Excretion of Beryllium
BeO calcinationtemperature in °C | Days after exposure | Cumulative excretion (% of initial lung burden) | % of total excretion | |
Feces | Urine | |||
500 | 32 | 24 +/-6 | 59 +/-2 | 41 +/-2 |
1000 | 32 | 18 +/-2 | 68 +/-3 | 32 +/-3 |
500 | 64 | 19+/-3 | 45 +/-6* | 55 +/-6* |
1000 | 64 | 21 +/-1 | 67 +/-6* | 33 +/-6* |
500 | 180 | 42 +/-8* | 47 +/-14 | 53 +/-14 |
1000 | 180 | 19 +/-4* | 54 +/-14 | 46 +/-14 |
N= 2 (32 and 64 days), N=4 (180 days)
* p<0.05
Table 2 Beryllium burden in selected tissues
Lungs | Tracheobronchial lymph nodes | Skeleton | Liver | Blood | ||
500 | 8 | 85 +/-6 | 0.6 +/-0.5 | 1.4 +/-0.8 | 0.1 +/-0.1 | 0.4 +/-0.1 |
1000 | 8 | 97 | 0.2 | 0.5 | 0.04 | 0.3 +/-0.1 |
500 | 32 | 77 +/-2* | 2.1 +/-2.2 | 2.5 +/-0.1 | 0.6 +/-0.1 | 0.4 +/-0.1 |
1000 | 32 | 97 +/-2* | 0.9 +/-0.2 | 0.4 +/-0.1 | 0.06 +/-0.09 | 0.2 +/-0.3 |
500 | 64 | 46 +/-8* | 8.8 +/-5.9 | 14 +/-4* | 2.3+/-1.0* | 1.0 +/-0.3 |
1000 | 64 | 88 +/-8* | 1.9 +/-1.1 | 1.5 +/-0.9* | 0.2 +/-0.1* | 0.3 +/-0.1 |
500 | 180 | 14 +/-2* | 1.8 +/-0.7 | 16+/-1* | 3.6 +/-0.5* | 1.6 +/-0.3 |
1000 | 180 | 62 +/-2* | 2.1 +/-0.9 | 3.1 +/-0.5* | 0.4+/-0.1* | 1.0 +/-0.2 |
* p<0.05
Applicant's summary and conclusion
- Conclusions:
- Interpretation of results (migrated information): high bioaccumulation potential based on study results
BeO is relatively persistent in the lungs. Calcination temperature affects the clearance rate from lung and body. Beryllium burden in tissues was generally low with levels of Be in skeleton being the highest - Executive summary:
Beagle dogs were exposed to BeO via inhalation. The BeO was calcined at either 500 or 1000 °C. Initial lung burdens of 17 or 50 ug/kg bodyweight was achieved. The levels of BeO in feces and urine was determined. Following sacrifice of animals, the level of BeO in tissues were determined. BeO was persistent in the lungs following inhalative exposure. Translocated BeO was primarily found in skeleteon, tracheobronchial lymph nodes, skeleton, liver and blood. Excretion of BeO was primarily in the feces at early timepoints and urine later (> 6 months). There was an effect of calcination temperature with BeO calcinated at 500C generally being cleared from the lung faster than BeO calcinated at 1000 °C. BeO calcinated at 500 °C was also generally associated with more severe pathological and immunological responses.
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