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EC number: 215-114-8 | CAS number: 1303-00-0
- 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
Repeated dose toxicity: other routes
Administrative data
- Endpoint:
- repeated dose toxicity: other route
- Remarks:
- other: non-standard test
- Type of information:
- experimental study
- Adequacy of study:
- disregarded due to major methodological deficiencies
- Reliability:
- 3 (not reliable)
- Rationale for reliability incl. deficiencies:
- other: see 'Remark'
- Remarks:
- No standard study design. Incomplete report of results, small animal number, no single values reported. Omura 1996b, Hamster (section 7.8.1) Omura et al. Testicular toxicity evaluation of arsenic-containing binary compound semiconductors, gallium arsenide and indium arsenide, in hamsters. Toxicol Lett 16, 1996b, 123-129. Hirata 1997, Hamster (section 7.1.1) Biomedical research on trace elements1997;8 191-192 In a first series of publications only data on reproduction toxicity of the male animals were published (Omura 1996, Hirata 1997). Tanaka et al. (2000): The missing data on systemic toxicity were published, showing slight to severe inflamatory responses in the lung and slight to mild lesions in the convoluted tubules of the kidney. These data on the lung weights indicate that the testicular changes are a consequence of a systemic impairment of the animals by the inflamatory reactions to GaAs in the lung.
Cross-reference
- Reason / purpose for cross-reference:
- reference to same study
Data source
Reference
- Reference Type:
- publication
- Title:
- Unnamed
- Year:
- 2 000
- Report date:
- 1999
Materials and methods
- Principles of method if other than guideline:
- The systemic and testicular toxicity of gallium arsenide (GaAs) was examined in Syrian golden hamsters rats by repetitive intratracheal instillation of this substance in suspension, twice a week for a total of 8 weeks (16 times).
- GLP compliance:
- no
Test material
- Reference substance name:
- gallium arsenide - mechanically destroyed material not marketed.
- IUPAC Name:
- gallium arsenide - mechanically destroyed material not marketed.
- Details on test material:
- - Name of test material (as cited in study report): gallium arsenide
- Physical state: solid, GaAs was pulverized finely and passed through a 400-mesh microsieve.
- Analytical purity: 99.9999%
- Impurities (identity and concentrations): GaAs powder contained 0.02% (wt%) of zirconium and a trace amount of yttrium. (contradictory data to the analytical purity)
- mean diameter: 1.32 µm
No further details are given.
Constituent 1
Test animals
- Species:
- hamster, Syrian
- Strain:
- not specified
- Sex:
- male
- Details on test animals or test system and environmental conditions:
- TEST ANIMALS
- Source: Japan SLC Inc., Hamamatsu, Japan
- Age at study initiation: approx. 12 weeks
- Weight at study initiation: mean +- SE: 124.9 +- 10.36 g (range 104.2-148.5) (Comment: this is the average weight of 30 hamsters of which 8 were used for GaAs instillation, the others were controls, instilled with InAs or As2O3)
- Diet. ad libitum, CE-2, Clea Japan Inc., Tokyo, Japan
- Water: ad libitum
- Fasting period before study: no
- Housing: 4 in a stainless steel cage
- Acclimation period: 6 weeks
ENVIRONMENTAL CONDITIONS
- Temperature (°C): 23 - 25 °C
- Humidity (%): 50 - 60 %
- Photoperiod (hrs dark / hrs light): 12/12
Administration / exposure
- Route of administration:
- other: intratracheal
- Vehicle:
- other: 1 ml/kg bw. phosphate buffer solution (0.025 M, pH 6.9)
- Details on exposure:
- After pretreatment with subcutaneous injection of 0.1 ml atropine sulfate /animal the powder of the test material was suspended in a phosphate buffer solution (PBS) and instilled into the trachea of rats anesthetised using ether.
- Analytical verification of doses or concentrations:
- no
- Duration of treatment / exposure:
- 8 weeks
- Frequency of treatment:
- 2 times a week, exact days not given, 16 instillations
Doses / concentrations
- Remarks:
- Doses / Concentrations:
0, 7.7 mg gallium arsenide/ kg bw.,
- Dose selection rationale:
- The total instillation dose of GaAs was 123.2 mg GaAs/ kg bw. and approximately the single dose used by Webb et al. (1986).
- No. of animals per sex per dose:
- 8 males only
- Control animals:
- yes, concurrent vehicle
- Details on study design:
- no data
Examinations
- Observations and examinations performed and frequency:
- body weights on the days of treatment
- Sacrifice and pathology:
- SACRIFICE
- The rats were sacrificed using an overdose of ether within 24 hours after the final instillation.
ORGAN WEIGHTS: Lung, spleen, kidney, liver
GROSS NECROPSY: no data
HISTOPATHOLOGY:
lung, spleen, liver, kidney,
The visceral organs were fixed in 10% neutral buffered formalin solution.
Fixed tissures were embedded in paraffin, cut into 6 µm sections, and stained with hematoxylin and eosin. Selected sections were stained with periodic acid Schiff (PAS), Elastica-van Gieson and Masson's trichrome.
- The right testis was fixed in Bouin's solution, embedded in paraffin, thinly sectioned, and stained with periodic acid Schiff reagent (PAS) and Mayer's hematoxylin.
- Degenerating germ cells at each stage of the cycle of the seminiferous epithelium were examined with the light microscope. Degenerating late elongated spermatids at stages IX, X, and XI were counted in all round or ovoid cross-sections of seminiferous tubules in one transverse section of the testis (18-50 cross-sections of the tubule).
- Nuclei of Sertoli cells were also counted.
- The count of degenerating elongated spermatids was expressed per tubule and per 100 Sertoli nuclei. In the statistical analysis of the count of degenerating spermatids, a mean value in one transverse section of the testis of the rat was treated as the representative value of that animal. - Statistics:
- - For body weight, testis weight, epididymal weight and sperm count, results were analyzed for mean and standard deviation and F-test was performed for evaluation equality of variance. If a significant difference was found in variance, t test with Welch's correction was used for statistical analysis, and t test without correction was used in other cases. In the case of the rate of abnormal sperm, Mann-Whitney test was used for statistical analysis. The results were interpreted as significant below a level of 0.05.
Fisher's least siginificant difference procedure was used in the case of body weight gain and organ weight after a one-way analysis of variance. In all statistical comparisons, a p value of less than 0.05 was used to indicate significant differences.
Results and discussion
Results of examinations
- Clinical signs:
- not specified
- Mortality:
- not specified
- Body weight and weight changes:
- no effects observed
- Food consumption and compound intake (if feeding study):
- not examined
- Food efficiency:
- not examined
- Water consumption and compound intake (if drinking water study):
- not examined
- Ophthalmological findings:
- not examined
- Haematological findings:
- not examined
- Clinical biochemistry findings:
- not examined
- Urinalysis findings:
- not examined
- Behaviour (functional findings):
- not examined
- Organ weight findings including organ / body weight ratios:
- effects observed, treatment-related
- Description (incidence and severity):
- increased lung weights, decreased kidney weights, reduction in epididymal sperm count, marked increase in abnormal sperm
- Gross pathological findings:
- not specified
- Histopathological findings: non-neoplastic:
- effects observed, treatment-related
- Description (incidence and severity):
- severe inflammatory changes in the lung, slight to mild progressive lesions in the convoluted tubules of the kidney
Target system / organ toxicity
- Critical effects observed:
- not specified
Applicant's summary and conclusion
- Conclusions:
- Omura 1996b, Hamster (section 7.8.1) Omura et al. Testicular toxicity evaluation of arsenic-containing binary compound semiconductors, gallium arsenide and indium arsenide, in hamsters. Toxicol Lett 16, 1996b, 123-129.
Hirata 1997, Hamster (section 7.1.1) Biomedical research on trace elements1997;8, 191-192
In a first series of publications only data on reproduction toxicity of the male animals were published (Omura 1996, Hirata 1997). Tanaka et al. (2000): The missing data on systemic toxicity were published, showing slight to severe inflamatory responses in the lung and slight to mild lesions in the convoluted tubules of the kidney. These results might indicate that the testicular changes are a consequence of a systemic impairment of the animals by the inflammatory reactions to GaAs in the lung.
Nowadays the incomplete report of study results would be a severe deviation from GLP-regulations - Executive summary:
Groups of 8 male Syrian golden hamsters were treated 2 times a week for 16 weeks with intratracheal instillations of 0 or 7.7 mg gallium arsenide/kg bw.. After pretreatment with a subcutanous injection of 0.1 ml atropine sulfate and anethesia with ether the intratracheal administration of 1 ml / kg bw. phosphate buffer solution containing suspended GaAs was done.
One day after the last instillation the animals were killed and autopsied.
Body weight: no differences to the control group,
Organ weights: significant increase in lung weight, significant decrease in the liver weight.
Histopathology: severe inflammatory changes in the lung, slight to mild progressive lesions in the convoluted tubules of the kidney.
These results might indicate that the testicular changes are a consequence of a systemic impairment of the animals by the inflamatory reactions to GaAs in the lung.
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