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EC number: 295-518-9 | CAS number: 92062-05-0 A complex combination of hydrocarbons obtained from the vacuum distillation of the products from a thermal cracking process. It consists predominantly of hydrocarbons having carbon numbers predominantly greater than C34 and boiling above approximately 495°C (923°F).
- 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 somatic cell study: cytogenicity / erythrocyte micronucleus
- Remarks:
- Type of genotoxicity: DNA damage and/or repair
- Type of information:
- migrated information: read-across from supporting substance (structural analogue or surrogate)
- Adequacy of study:
- key study
- Reliability:
- 2 (reliable with restrictions)
Data source
Reference
- Reference Type:
- publication
- Title:
- Importance of DNA - adduct formation and gene expression profiling of disease candidate genes in rats exposed to bitumen fumes
- Author:
- Halter R, Hansen T, Seidel A, Ziemann C, Borlak J
- Year:
- 2 007
- Bibliographic source:
- Journal of Occupational and Environmental Hygiene, 4 (S1), p 44-64
Materials and methods
Test guideline
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 474 (Mammalian Erythrocyte Micronucleus Test)
- Principles of method if other than guideline:
- Micronucleus formation in peripheral blood and bone marrow
- GLP compliance:
- not specified
- Type of assay:
- micronucleus assay
Test material
- Reference substance name:
- Asphalt, oxidized
- EC Number:
- 265-196-4
- EC Name:
- Asphalt, oxidized
- Cas Number:
- 64742-93-4
- IUPAC Name:
- Asphalt, oxidized
- Test material form:
- other: low viscosity hydrocarbon liquid
- Details on test material:
- test material was a paving grade bitumen
Constituent 1
Test animals
- Species:
- rat
- Strain:
- Wistar
- Sex:
- male/female
- Details on test animals or test system and environmental conditions:
- TEST ANIMALS
- Source: no information provided
- Age at study initiation: ~ 5 weeks
- Weight at study initiation: no information provided
- Assigned to test groups randomly: yes, by weight
- Fasting period before study: no information provided
- Housing: two / cage
- Diet (e.g. ad libitum): Altomin 1324N ad-lib
- Water (e.g. ad libitum): tap water ad-lib
- Acclimation period: no information provided
ENVIRONMENTAL CONDITIONS
- Temperature (°C): 22 +/- 2C
- Humidity (%): 40-70%
- Air changes (per hr): 12-15
- Photoperiod (hrs dark / hrs light): 12:12
IN-LIFE DATES: From: To: no information provided
Administration / exposure
- Route of administration:
- inhalation
- Vehicle:
- dilution air
- Details on exposure:
- Animals were exposed by nose only inhalation to a mixture of aerosol and vapour, generated using an evaportion condensation generator. Exposures were for 4hrs/day, 5 days/week for up to 2 years.
Periheral blood samples were take after 5 days, 1 month and 12 months for micronucleus assessment in erythrocytes
Bone marrow samples were taken after 12 months exposure for micronucleus assessment. - Duration of treatment / exposure:
- Up to 104 weeks.
- Frequency of treatment:
- 4hrs/day, 5 days/week
- Post exposure period:
- none specifed
Doses / concentrationsopen allclose all
- Remarks:
- Doses / Concentrations: 0, 4, 20, 100 mg/m3
Basis: nominal conc.
- Remarks:
- Doses / Concentrations: 0, 4.1, 20.7, 103.9 mg/m3
Basis: analytical conc. BIA method
- Remarks:
- Doses / Concentrations: 0, 6.8, 34.4, 172.5 mg/m3
Basis: other: converted absolute concentration (calculated from analytical concentrations using a factor of 1.66 for the difference between absolute bitumen fume concentration and the concentration determined using the BIA method 6305. (BIA method understimates conscentration due to the internal standard used - mineral oil rather than bitumen fume standard)
- Control animals:
- yes, sham-exposed
- Positive control(s):
- none specified
Examinations
- Tissues and cell types examined:
- Peripheral blood - polychromatic erythtrocytes
Bone marrow - polychromatic erythtrocytes - Details of tissue and slide preparation:
- Lithium-heparin treated blood samples were smeared on glass slides and stained with Grunald and Geisma solution for microscopic analysis.
Bome marrow cells were harvested to produce a cell suspension that was smeared on glass slides and stained with Grunwald and Geisma solution for microscopic analysis. - Evaluation criteria:
- Comparison of control and bitumen treated animals
- Statistics:
- No information provided
Results and discussion
Test results
- Sex:
- male/female
- Genotoxicity:
- negative
- Remarks:
- Bone marrow micronucleus and peripheral blood
- Toxicity:
- no effects
- Vehicle controls validity:
- valid
- Negative controls validity:
- not examined
- Positive controls validity:
- not examined
Applicant's summary and conclusion
- Conclusions:
- Interpretation of results (migrated information): negative Periheral blood erythrocyte micronucleus and bone marrow micronucleus
There was no evidence of increased micronucleu formation in rat bone marrow and peripheral blood cells following up to 12 months exposure to bitumen fumes. - Executive summary:
Male and female rats were exposed by inhalation to a mixture of aerosol and vapour derived from a bitumen fume condensate, collected from a heated storage tank. Following periods of exposure of up to 12 months, there was no evidence of increased micronucleus formation in bone marrow and peripheral blood cells.
Systemic exposure to bitumen fumes was confirmed by presence of PAH metabolites in urine, increased metabolising activity in lung, DNA adducts in respirtatory tissue and repression of RBCcount in bone marrow.
Exposure to bitumen fumes was not genotoxic in an in-vivo micronucleus assay.
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