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EC number: 265-198-5 | CAS number: 64742-94-5 A complex combination of hydrocarbons obtained from distillation of aromatic streams. It consists predominantly of aromatic hydrocarbons having carbon numbers predominantly in the range of C9 through C16 and boiling in the range of approximately 165°C to 290°C (330°F to 554°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:
- migrated information: read-across based on grouping of substances (category approach)
- Adequacy of study:
- key study
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- other: Non-GLP, non-guideline, animal experimental study, restrictions in design and/or reporting but otherwise adequate for assessment
Cross-referenceopen allclose all
- Reason / purpose for cross-reference:
- reference to same study
- Reason / purpose for cross-reference:
- reference to other study
Data source
Reference
- Reference Type:
- publication
- Title:
- Mutagenicity of 1,3-butadiene inhalation in somatic and germinal cells of mice.
- Author:
- Adler I-D, Cao J, Filser JG, Gassner P, Kessler W, Kliesch U, Neuhäuser-Klaus A, Nüsse M.
- Year:
- 1 994
- Bibliographic source:
- Mutat Res. 309; 307-314.
Materials and methods
Test guideline
- Qualifier:
- equivalent or similar to guideline
- Guideline:
- OECD Guideline 474 (Mammalian Erythrocyte Micronucleus Test)
- Deviations:
- not specified
- Principles of method if other than guideline:
- not applicable
- GLP compliance:
- not specified
- Type of assay:
- micronucleus assay
Test material
- Reference substance name:
- 1,3-butadiene
- IUPAC Name:
- 1,3-butadiene
- Details on test material:
- - Name of test material (as cited in study report): 1,3-butadiene
- Purity: 99.5%
- Source: Linde, Unterschleissheim, Germany
Constituent 1
Test animals
- Species:
- mouse
- Strain:
- other: 102/E1 x C3H/E1)F1
- Sex:
- male/female
- Details on test animals or test system and environmental conditions:
- TEST ANIMALS
- Source: GSF animal colony
- Age at study initiation: 10-12 weeks
- Weight at study initiation: The average weight of groups of 20 animals before exposure was: 26.7 ± 1.0 g(control), 25.6 ± 0.9 g (50 ppm), 26.4 ± 1.0 g (200 ppm), 25.6 ± 0.8 g (500 ppm) and 26.1 ± 1.0 g (1300 ppm).
- Housing: 10 sex/group
- Diet: Altronin ad libitum except for during, and for 1 hour following exposure
- Water: ad libitum
- Acclimation period: 1 week
ENVIRONMENTAL CONDITIONS IN CHAMBERS
- The chambers were supplied with a stream (80 1/min) of charcoal-filtered and climatized air (25°C, 55% moisture)
IN-LIFE DATES: no data
Administration / exposure
- Route of administration:
- inhalation: gas
- Vehicle:
- air
- Details on exposure:
- TYPE OF INHALATION EXPOSURE: whole body
GENERATION OF TEST ATMOSPHERE / CHAMBER DESCRIPTION
- Exposure apparatus: glass chambers (240 L) with room for two stainless steel wire cages (65 x 40 X 12 cm).
- System of generating test atmosphere: 1,3-butadiene was metered at a known and constant flow rate into the air stream to achieve the desired exposure concentration.
TEST ATMOSPHERE
- Brief description of analytical method used: Septa for air sampling were positioned 30 cm before the inlet and behind the outlet of the chamber. The atmosphere was analyzed for 1,3-butadiene concentration at 15-min intervals during the first hour of daily exposure and at 30-min intervals thereafter by gas chromatography.
- Samples taken from breathing zone: yes - Duration of treatment / exposure:
- 6 h per day for 5 consecutive days
- Frequency of treatment:
- Daily
- Post exposure period:
- None
Doses / concentrations
- Remarks:
- Doses / Concentrations:
50, 200, 500 or 1300 ppm
Basis:
nominal conc.
- No. of animals per sex per dose:
- Bone marrow micronucleus test: 5 per sex
Peripheral blood micronucleus test: 2 per sex - Control animals:
- yes, concurrent no treatment
- Positive control(s):
- none
Examinations
- Tissues and cell types examined:
- Bone marrow and peripheral blood
- Details of tissue and slide preparation:
- BONE MARROW MICRONUCLEUS TEST
TREATMENT AND SAMPLING TIMES:
- Bone marrow was sampled 18-24 h after the end of exposure.
DETAILS OF SLIDE PREPARATION:
- Bone marrow preparation, staining and scoring were performed (Adler, 1984).
METHOD OF ANALYSIS:
- Per animal 2000 polychromatic erythrocytes (PCE) were scored microscopically for the presence of micronuclei and the means were expressed as micronucleated PCE (MPE) per 1000 PCE.
- To determine a shift in erythroblast proliferation the number of PCE was counted in the microscope fields that contained 2000 normochromatic erythrocytes (NCE) and the mean values are expressed as % PCE of the total erythrocyte counts. Micronucleated NCE were also recorded.
PERIPHERAL BLOOD MICRONUCLEUS TEST
TREATMENT AND SAMPLING TIMES:
- Blood (30-50 µL) was collected from the orbital vein of mice into heparinized tubes
- The samples were taken 18-24h after the end of the exposure to 0, 50, 200 and 1300 ppm of 1,3-butadiene.
METHOD OF ANALYSIS:
- A sample of 5 µL of blood was used for two measurements per animal. Dual laser flow cytometry and sorting was performed.
SCORING:
- Microscopic scoring: For comparison, the blood samples were also scored microscopically using the acridine orange supravital staining method of Hayashi et al. (1990). For each animal, 1000 type I, II and III PCE (Vander et al 1963) were scored for the presence of micronuclei. Samples from exposure groups, 0, 50, 200 and 1300 ppm were analyzed. - Evaluation criteria:
- see below
- Statistics:
- Significance of differences between exposure groups was determined with the Mann-Whitney test (Sachs, 1974). The dose response was determined by regression analysis.
Results and discussion
Test results
- Sex:
- male/female
- Genotoxicity:
- positive
- Remarks:
- Bone marrow micronucleus
- Additional information on results:
- none
Any other information on results incl. tables
The buta-1,3-diene chamber concentrations did not deviate more than 12% at 50 ppm, 1% at 200 ppm, 0.2% at 500 ppm and 2% at 1300 ppm from the nominal concentration throughout the exposure duration.
The micronucleus frequency in bone marrow PCE increased with exposure concentration. The lowest exposure concentration caused a significant increase over the control level (p < 0.01, Mann-Whitney test). The slope of the dose-response curve did not remain constant but flattened with increasing concentration. In the concentration range between 500 and 1300 ppm only a small rise of the micronucleus frequency of about 17% was found. At 500 and 1300 ppm the response of the males was higher than that of the exposed females (p < 0.05, Mann-Whitney test). 1,3-Butadiene exposure had no effect on erythroblast proliferation.
Results of bone marrow micronucleus test
Concentration (ppm) |
Individual animal counts MPE/2000 PCE |
Mean MPE (% ±SD) |
PCE (%) |
|
Male |
Female |
|||
0 |
1, 1, 3, 4, 6 |
1, 1, 1, 1, 6 |
1.3 ± 0.6 |
49.0 |
50 |
8, 9, 10, 12, 17 |
8, 9, 10, 10, 14 |
5.4 ± 1.0 |
49.6 |
200 |
19, 21, 24, 26, 27 |
13, 16, 18, 20, 25 |
10.5 ± 1.4 |
49.1 |
500 |
35, 35, 36, 42, 44 |
24, 24, 30, 31, 32 |
16.7 ± 1.8* |
49.7 |
1300 |
39, 40, 43, 46, 53 |
28, 32, 33, 37, 39 |
19.5 ± 1.6* |
49.6 |
*The male response was significantly higher than the female response (p<0.05)
The micronucleus frequency in PCE of peripheral blood also increased with exposure concentration. When scored manually the same sensitivity difference as in the bone marrow micronucleus test between males and females was obvious at 200 and 1300 ppm. The dose-response curve had approximately the same shape. There was no difference between the micronucleus yields in bone marrow and peripheral blood, the latter scored either manually or by flow cytometry.
Applicant's summary and conclusion
- Conclusions:
- Interpretation of results (migrated information): positive
The data demonstrate that Inhalation exposure of mice to 1,3-butadiene (50, 200, 500 or 1300 ppm for 6 h per day for 5 days) induced micronuclei in bone marrow and peripheral blood, with male mice more sensitive than females at the higher exposure concentrations. The dose-response curve is consistent with the metabolism of 1,3-butadiene to epoxides, which may then induce micronuclei. - Executive summary:
Inhalation exposure of mice to 50, 200, 500 or 1300 ppm (110, 442, 1106 or 2876 mg/m3) of 1,3 -butadiene for 6 h per day for 5 consecutive days caused micronuclei in mouse bone marrow and peripheral blood erythrocytes. The dose response was non-linear. The slope of the curve flattened with increasing exposure concentration.
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