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EC number: 309-870-9 | CAS number: 101316-66-9 A complex combination of hydrocarbons obtained during the sorptions of toluene from a hydrocarbon fraction from cracked gasoline treated with hydrogen in the presence of a catalyst. It consists predominantly of hydrocarbons having carbon numbers predominantly in the range of C6 through C8 and boiling in the range of approximately 80°C to 135°C (176°F to 275°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: chromosome aberration
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- other: Guideline study, available as unpublished report, no restrictions, fully adequate for assessment
Data source
Reference
- Reference Type:
- study report
- Title:
- Unnamed
- Year:
- 2 004
- Report date:
- 2004
Materials and methods
Test guidelineopen allclose all
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 474 (Mammalian Erythrocyte Micronucleus Test)
- Deviations:
- no
- Qualifier:
- according to guideline
- Guideline:
- EU Method B.12 (Mutagenicity - In Vivo Mammalian Erythrocyte Micronucleus Test)
- Deviations:
- no
- Qualifier:
- according to guideline
- Guideline:
- EPA OPPTS 870.5395 (In Vivo Mammalian Cytogenetics Tests: Erythrocyte Micronucleus Assay)
- Deviations:
- no
- GLP compliance:
- yes (incl. QA statement)
- Type of assay:
- micronucleus assay
Test material
- Reference substance name:
- Hydrocarbons, C5-rich
- EC Number:
- 270-695-5
- EC Name:
- Hydrocarbons, C5-rich
- Cas Number:
- 68476-55-1
- IUPAC Name:
- 68476-55-1
- Reference substance name:
- Pyrolysis C5s
- IUPAC Name:
- Pyrolysis C5s
- Reference substance name:
- C5, noncyclics
- IUPAC Name:
- C5, noncyclics
- Reference substance name:
- 68476-43-7, 68527-19-5, 68603-00-9 and 68956-55-8
- IUPAC Name:
- 68476-43-7, 68527-19-5, 68603-00-9 and 68956-55-8
- Details on test material:
- - Name of test material (as cited in study report): pyrolysis C5s
- Substance type: complex mixture of hydrocarbons
- Physical state: clear, colourless liquid
- Lot/batch No.: QA1001A100
- Expiration date of the lot/batch: Not provided by Sponsor
- Stability under test conditions: The 3 major components analysed were shown to be stable for the duration of the study
- Storage condition of test material: approximately 10°C in the dark under nitrogen
- The sample tested consisted of isoprene (18%), cis- and trans-pentadiene-1, 3 (16%), cyclopentadiene + dicyclopentadiene (14%), n-pentane (10%), cyclopentene (7%), 2-methy1-2-butene (3%) and cyclopentane (1%)
- The balance consists of other hydrocarbons with similar boiling point (primarily C5s)
Constituent 1
Constituent 2
Constituent 3
Constituent 4
Test animals
- Species:
- mouse
- Strain:
- CD-1
- Sex:
- male
- Details on test animals or test system and environmental conditions:
- TEST ANIMALS
- Source: Charles River UK Limited, Margate, Kent, UK
- Age at study initiation: Not reported
- Weight at study initiation: 29.4-35.2 g
- Assigned to test groups randomly: yes
- Housing: Group housed
- Diet: pelleted expanded rat and mouse No.1 maintenance diet (SQC grade obtained from Special Diets Services Ltd, Witham, Essex, UK) ad libitum (except during exposures)
- Water: tap water ad libitum (except during exposures)
- Acclimation period: Minimum of 6 days
ENVIRONMENTAL CONDITIONS
- Temperature: 21±2°C
- Humidity: 55±10%
- Air changes (per hr): Not reported
- Photoperiod: 12hrs dark / 12hrs light
IN-LIFE DATES: From: 12 June 2002 To: 13 June 2002
Administration / exposure
- Route of administration:
- inhalation: vapour
- Vehicle:
- - Vehicle(s)/solvent(s) used: air
- Details on exposure:
- TYPE OF INHALATION EXPOSURE: whole body
GENERATION OF TEST ATMOSPHERE / CHAMBER DESCRIPTION
- Exposure apparatus: Glass vapour generators
- Compressed air was used to generate atmospheres for both negative control and test chemical exposed groups. Gas chromatography was used to measure the concentrations of Pyrolysis C5s in the test atmospheres. Negative control animals were exposed using compressed air. - Duration of treatment / exposure:
- 2 days
- Frequency of treatment:
- Daily (two 6-hour exposures on consecutive days)
- Post exposure period:
- 24 hours after 2nd exposure period
Doses / concentrationsopen allclose all
- Remarks:
- Doses / Concentrations:
40, 125 and 500 ppm
Basis:
other: target concentration
- Remarks:
- Doses / Concentrations:
44, 130 and 490 ppm
Basis:
analytical conc.
- No. of animals per sex per dose:
- 7 control and treated
5 positive control - Control animals:
- yes, sham-exposed
- Positive control(s):
- mitomycin C
- Route of administration: oral gavage
- Doses / concentrations: 12 mg/kg
Examinations
- Tissues and cell types examined:
- micronuclei (MN) in polychromatic erythrocytes (PCE)
- Evaluation criteria:
- One smear from each animal was examined for the presence of micronuclei in 2000 immature erythrocytes. The proportion of immature erythrocytes was assessed by examination of at least 1000 erythrocytes from each animal and the incidence of micronucleated mature erythrocytes was recorded. A positive response is normally indicated by a statistically significant dose-related increase in the incidence of micronucleated immature erythrocytes for the treatment group compared with the concurrent control group (P<0.01); individual and/or group mean values should exceed the laboratory historical control range (Morrison and Ashby 1995). A negative result is indicated where individual and group mean incidences of micronucleated immature erythrocytes for the group treated with the test substance are not significantly greater than incidences for the concurrent control group (P>0.01) and where these values fair within the historical control range. An equivocal response is obtained when the results do not meet the criteria specified for a positive or negative response. Bone marrow cell toxicity (or depression) is normally indicated by a substantial and statistically significant dose-related decrease in the proportion of immature erythrocytes (P<0.01).
- Statistics:
- Incidences of micronucleated immature erythrocytes: Linear-by-Linear association test and exact one tailed pairwise Permutation test.
Proportion of immature erythrocytes: exact versions of Wilcoxon's sum of ranks test and Jonckheere's test for trend.
Results and discussion
Test results
- Sex:
- male
- Genotoxicity:
- negative
- Toxicity:
- no effects
- Negative controls validity:
- valid
- Positive controls validity:
- valid
Any other information on results incl. tables
No clinical signs or mortalities were observed for any animal treated with Pyrolysis C5s and killed 24 hours after two 6-hour periods of whole body inhalation exposure, compared to negative control values (P>0.01 in each case). No statistically significant increases in the frequency of micronucleated immature erythrocytes and no substantial decreases in the proportion of immature erythrocytes were recorded.
Applicant's summary and conclusion
- Conclusions:
- Interpretation of results (migrated information): negative
Pyrolysis C5s did not show any evidence of causing chromosome damage or bone marrow cell toxicity when administered by whole body inhalation exposure in an in vivo mouse micronucleus test. - Executive summary:
Groups of 7 male CD-1 mice were exposed to Pyrolysis C5s (CAS 68476 -55 -1) for two 6-hour whole body exposure periods, on consecutive days, at target concentrations of 40, 150 and 500 ppm. Negative control animals were exposed using compressed air. A positive control group (5 animals) were dosed once only by oral gavage with mitomycin C at 12 mg/kg. All animals were sacrificed approximately 24 hours after the second exposure period (24 hours after the oral dose for the positive control group) and bone marrow smears prepared. Smears were examined to evaluate the incidence of micronuclei in 2000 polychromatic erythrocytes (PCE) per animal. The proportion of PCE was assessed by examination of at least 1000 erythrocytes.
No statistically significant increase in the incidence of micronucleated PCE were observed in the Pyrolysis C5s exposed animals compared with the negative control values. The positive control treatment induced a significant increase.
The results demonstrate that Pyrolysis C5s is not clastogenic toward mammalian cells in vivo.
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