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EC number: 292-604-8 | CAS number: 90640-82-7 The oil remaining after the removal, by a crystallization process, of an anthracene-rich solid (anthracene paste) from anthracene oil. It is composed primarily of two, three and four membered aromatic compounds.
- 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 vitro
Administrative data
- Endpoint:
- in vitro cytogenicity / chromosome aberration study in mammalian cells
- Remarks:
- Type of genotoxicity: chromosome aberration
- Type of information:
- migrated information: read-across from supporting substance (structural analogue or surrogate)
- Adequacy of study:
- key study
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- other: Guideline study with acceptable restrictions
Data source
Reference
- Reference Type:
- study report
- Title:
- Unnamed
- Year:
- 1 991
- Report date:
- 1991
Materials and methods
Test guideline
- Qualifier:
- equivalent or similar to guideline
- Guideline:
- OECD Guideline 473 (In Vitro Mammalian Chromosome Aberration Test)
- Deviations:
- yes
- Remarks:
- Only one cultivation instead of two was conducted per test series (no duplicate).
- GLP compliance:
- yes
- Type of assay:
- in vitro mammalian chromosome aberration test
Test material
- Reference substance name:
- Creosote
- EC Number:
- 232-287-5
- EC Name:
- Creosote
- Cas Number:
- 8001-58-9
- IUPAC Name:
- 8001-58-9
- Details on test material:
- - Creosote WEI-Type B
- Name of test material (as cited in study report): Creosote Spéciale 14130
- Molecular formula (if other than submission substance): not applicable, UVCB
- Substance type: organic
- Physical state: liquid
- Composition:
[w/w%]
=========================
Aromatic hydrocarbons 89.7
Phenols 6.8
N-Compounds 3.4
Benzene 0.04
Toluene 0.22
Ethyl-Benzene 0.21
m/p-Xylene 0.70
Styrene 0.12
o-Xylene 0.24
Indane 3.1
Indene 2.9
Naphthalene 12.2
2-Me-Naphthalene 5.3
1-Me-Naphthalene 3.3
Diphenyl 2.7
Acenaphthene 12.6
Fluorene 10.3
Phenanthrene 4.6
Anthracene 1.2
Fluoranthene 0.7
B(a)P 15 ppm
B(a)A 40 ppm
B(b)F 15 ppm
B(h)F + B(j)F 10 ppm
DiB(a, h)A < 5 ppm
Phenol 0.5
o-cresol 1.7
p-cresol 1.4
m-cresol 1.6
Xylenols 1.3
===========================
Constituent 1
Method
Species / strain
- Species / strain / cell type:
- lymphocytes: human
- Metabolic activation:
- with and without
- Metabolic activation system:
- microsomes derived from Arochlor1254-induced rat liver (male SD rats, 500 mg/kg i.p. 5 d prior to sacrifice)
Controls
- Negative solvent / vehicle controls:
- yes
- Positive controls:
- yes
- Remarks:
- + S9: cyclophosphamide (0.02 mg/mL)- S9: methyl methanesulphonate (0.05 mg/mL)
Results and discussion
Test results
- Species / strain:
- lymphocytes: human
- Metabolic activation:
- with and without
- Genotoxicity:
- negative
- Cytotoxicity / choice of top concentrations:
- cytotoxicity
- Remarks:
- 0.15 mg/mL and 0.25 mg/mL highest concentrations exhibiting a reduction of the mitotic index of about 50 % and between 90.5 and 82.6 %, respectively.
- Vehicle controls validity:
- valid
- Positive controls validity:
- valid
- Remarks on result:
- other: all strains/cell types tested
- Remarks:
- Migrated from field 'Test system'.
Any other information on results incl. tables
Summary of cytogenetic In-Vitro-Test: Chromosomal Analysis
Vehicle control |
0.05 mg/ml |
0.1 mg/ml |
0.15 mg/ml |
0.25 mg/ml |
|||||||
cytotoxicity |
no |
no |
no |
Yes |
Yes |
||||||
Metaphases scored (1sttest / 2ndtest) |
100 / 100 |
100 / 100 |
100 / 100 |
100 / 100 |
100 / 100 |
100 / 100 |
- / 100 |
- / 100 |
19 / 97 |
38 / 38 |
|
-S9 |
+S9 |
-S9 |
+S9 |
-S9 |
+S9 |
-S9 |
+S9 |
-S9 |
+S9 |
||
chromatid aberrations |
Gaps (TG)1)2) |
1 / 3 |
3 / 2 |
1 / 0 |
3 / 1 |
1 / 2 |
2 / 0 |
- / 1 |
- / 2 |
0 / 4 |
2 / 0 |
Breaks (TB)2) |
0 / 0 |
3 / 1 |
0 / 1 |
1 / 2 |
1 / 1 |
0 / 4 |
- / 1 |
- / 1 |
0 / 0 |
1 / 0 |
|
interchanges |
0 / 0 |
0 / 0 |
0 / 0 |
0 / 0 |
0 / 0 |
0 / 0 |
0 / 0 |
0 / 0 |
0 / 0 |
0 / 0 |
|
Isochromatid aberrations |
Gaps (SG)1)2) |
0 / 2 |
1 / 0 |
1 / 0 |
0 / 0 |
1 / 1 |
0 / 0 |
- / 0 |
- / 0 |
0 / 1 |
0 / 1 |
Breaks (SB)2) |
1 / 1 |
2 / 1 |
2 / 1 |
0 / 1 |
0 / 1 |
0 / 1 |
- / 4 |
- / 6 |
0 / 4 |
0 / 0 |
|
interchanges |
0 / 0 |
0 / 0 |
0 / 0 |
0 / 0 |
0 / 0 |
0 / 0 |
0 / 0 |
0 / 0 |
0 / 0 |
0 / 0 |
|
uncoiled chromatin (UC)2) |
0 / 0 |
0 / 0 |
0 / 0 |
0 / 0 |
0 / 0 |
1 / 0 |
- / 0 |
- / 0 |
0 / 0 |
0 / 0 |
|
mitotic index |
4.2 / 5.4 |
4.6 / 5.4 |
5.4 / 6.0 |
4.4 / 5.0 |
4.2 / 4.6 |
4.6 / 4.2 |
- / 2.4 |
- / 3.0 |
0.4 / 1.4 |
0.8 / 1.2 |
|
polyploidy |
0 / 0 |
0 / 0 |
0 / 0 |
0 / 0 |
0 / 0 |
0 / 0 |
- / 0 |
- / 0 |
0 / 0 |
0 / 0 |
|
endo reduplication |
0 / 0 |
0 / 0 |
0 / 0 |
0 / 0 |
0 / 0 |
0 / 0 |
- / 0 |
- / 0 |
0 / 0 |
0 / 0 |
|
Mean number of aberrations per cells |
0.01 / 0.01 |
0.05 / 0.02 |
0.02 / 0.02 |
0.01 / 0.03 |
0.01 / 0.02 |
0.00 / 0.05 |
- / 0.05 |
- / 0.07 |
0.00 / 0.04 |
0.03 / 0.00 |
|
CH2test results |
-- |
-- |
0.34 / 0.34 |
1.85 / 0.21 |
0.00 / 0.34 |
4.08 / 1.33 |
- / 1.85 |
- / 0.69 |
0.19 / 1.94 |
0.15 / 0.77 |
MI = Mitotic index;
1)not included in total aberration frequency
2)TB, TG, SB, SB, UC = Abbreviations used in tables of the test report
----------------------------------------
The selected test concentrations clearly covered a cytotoxic range, with about 50 % depression of the mitotic index at the additional concentration of 0.15 mg/ml, as compared to vehicle control and the lower test levels.
Under the test conditions, the creosote WEI Type B (containing <50 ppm BaP) did not induce chromosome aberrations in human lymphocytes in culture in the presence and absence of metabolic activation. Based upon the CHI-square test (p <0.01), no statistical significance was found as compared with the vehicle control. Metabolic activation had no noticeable influence on the aberration spectrum and yield. The positive controls showed significant increases in aberration frequencies.
Applicant's summary and conclusion
- Conclusions:
- Interpretation of results (migrated information):
negative - Executive summary:
A creosote containing less than 50 ppm BaP was tested according to standard guidelinesOECD 473 (1983) and EEC Directive 84/449, B.10 (1984). Blood had been obtained from healthy non-smoking volunteers, and lymphocytes were proliferated and stimulated through cultivation with phytohaemagglutinin (48 h). Exposure time was 3 h, post-exposure time 22 h. Cell growth was stopped by addition of colchicine (2 h incubation). In a preliminary test, the cytotoxic potential of the creosote was estimated (mitotic index without S9, based on 500 cells per concentration). A confirmatory second independent main study was performed without variation of culture parameters (except a further test concentration: see below).
In the second test series, a further test concentration (0.15 mg/ml) was introduced as 3rdof 4 concentrations, because the highest one previously selected proved to be too cytotoxic in the 1sttest series.
Besides examination of chromosomal aberrations, the mitotic index was concurrently determined for each concentration tested. Gaps were recorded, but not included in the final result of aberration frequency. Under the test conditions, the creosote WEI Type B (containing <50 ppm BaP) did not induce chromosome aberrations in human lymphocytes in culture in the presence and absence of metabolic activation. Based upon the CHI-square test (p <0.01), no statistical significance was found as compared with the vehicle control. Metabolic activation had no noticeable influence on the aberration spectrum and yield. The positive controls showed significant increases in aberration frequencies.
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