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EC number: 905-287-4 | CAS number: 1638758-52-7
- 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 gene mutation study in bacteria
- Remarks:
- Type of genotoxicity: gene mutation
- Type of information:
- read-across based on grouping of substances (category approach)
- Adequacy of study:
- weight of evidence
- Justification for type of information:
- No data are available for the target substance. Studies of genotoxicity in vitro with the individual (o-, m- and p-) cresol isomers report negative results in Ames tests and mammalian cell mutation assays and positive results in studies of chromosomal aberration in vitro. Studies of genotoxicity in vivo report negative results. Studies of genotoxicity in vitro with xylenol (mixed isomers) report negative results in Ames tests and mammalian cell mutation assays and positive results in studies of chromosomal aberration in vitro. Studies of genotoxicity in vivo report negative results for 3,5-, 2,4- and 2,6-xylenol. Based on the consistent response seen for the source substances, it can be concluded that the target substance is also not genotoxic.
Data source
Materials and methods
Test guideline
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 471 (Bacterial Reverse Mutation Assay)
- Deviations:
- no
- GLP compliance:
- yes
- Type of assay:
- bacterial reverse mutation assay
Test material
- Reference substance name:
- Reaction mass of 2,4-xylenol and 2,5-xylenol
- EC Number:
- 905-287-4
- Cas Number:
- 1638758-52-7
- Molecular formula:
- (CH3)2C6H3OH
- IUPAC Name:
- Reaction mass of 2,4-xylenol and 2,5-xylenol
- Test material form:
- solid: bulk
Constituent 1
Method
Species / strainopen allclose all
- Species / strain / cell type:
- S. typhimurium TA 1535, TA 1537, TA 98 and TA 100
- Additional strain / cell type characteristics:
- not specified
- Species / strain / cell type:
- E. coli WP2 uvr A
- Additional strain / cell type characteristics:
- not specified
- Metabolic activation:
- with and without
- Metabolic activation system:
- S9 derived from Aroclor 1254 induced male Sprague-Dawley rats
- Test concentrations with justification for top dose:
- 6.7, 10, 33, 67, 100, 333, 667, 1000, 3333 and 5000 µg/plate for strains TA98, TA100, TA1535, TA1537 and WP2 uvrA for the preliminary toxicity study (with and without metabolic activation).75, 200, 600, 1800 and 5000 µg/plate for TA98, TA100, TA1535, TA1537 and WP2 uvrA for the bacterial mutation assay (with and without metabolic activation).
- Vehicle / solvent:
- - Vehicle(s)/solvent(s) used: dimethyl sulfoxide (DMSO) (and water for sodium azide dilution in the positive control)- Justification for choice of solvent/vehicle: Not stated, commonly used solvent
Controls
- Untreated negative controls:
- no
- Negative solvent / vehicle controls:
- yes
- True negative controls:
- no
- Positive controls:
- yes
- Positive control substance:
- other:
- Remarks:
- 2-aminoanthracene for WP2 uvrA in the presence of metabolic activation. 2-nitroluorene for TA98; sodium azide for TA100 and TA1535; 9-aminoacridine for TA1537; methyl methanesulfonate for WP2 uvrA in the absence of metabolic activation.
- Details on test system and experimental conditions:
- METHOD OF APPLICATION: in agar (plate incorporation)DURATION- Preincubation period: 12 hours- Exposure duration: 48 - 72 hours- Expression time (cells in growth medium): not stated- Fixation time (start of exposure up to fixation or harvest of cells): not stated
- Evaluation criteria:
- All cultures must demonstrate the characteristic mean number of spontaneous revertants in the vehicle controls.The mean of each positive control must exhibit at least a 3.0 fold increase in the number of revertants over the mean value of the respective control. A minimum of three non toxic dose levels is required for evaluation. A dose level is considered to be toxic if there is a >50% reduction in the mean number of revertants per plate compared to the mean vehicle control value and at least a moderate reduction in the background lawn.
Results and discussion
Test resultsopen allclose all
- Species / strain:
- S. typhimurium TA 1535, TA 1537, TA 98 and TA 100
- Metabolic activation:
- with and without
- Genotoxicity:
- negative
- Cytotoxicity / choice of top concentrations:
- not specified
- Vehicle controls validity:
- valid
- Untreated negative controls validity:
- not applicable
- Positive controls validity:
- valid
- Species / strain:
- E. coli WP2 uvr A
- Metabolic activation:
- with and without
- Genotoxicity:
- negative
- Cytotoxicity / choice of top concentrations:
- not specified
- Vehicle controls validity:
- valid
- Untreated negative controls validity:
- not applicable
- Positive controls validity:
- valid
- Additional information on results:
- COMPARISON WITH HISTORICAL CONTROL DATA: Historical control data were found to support the study outcome.
- Remarks on result:
- other: all strains/cell types tested
- Remarks:
- Migrated from field 'Test system'.
Any other information on results incl. tables
The results of the genotoxicity study found that mixed xylenols were not genotoxic at any dose level tested. A summary of the results is presented below.
Table 1: Summary of results of the mutagenicity assay
Dose (µg/plate) |
Average revertants per plate ± standard deviation |
||||
TA98 |
TA100 |
TA1535 |
TA1537 |
WP2 uvrA |
|
In the absence of metabolic activation |
|||||
Vehicle control |
17 ± 2 |
153 ± 13 |
16 ± 2 |
7 ± 2 |
24 ± 3 |
75 |
14 ± 5 |
126 ± 3 |
23 ± 5 |
7 ± 1 |
24 ± 2 |
200 |
17 ± 2 |
126 ± 31 |
19 ± 4 |
6 ± 2 |
20 ± 5 |
600 |
14 ± 5 |
133 ± 26 |
19 ± 2 |
6 ± 1 |
15 ± 3 |
1800 |
16 ± 3 |
125 ± 11 |
21 ± 7 |
4 ± 1 |
13 ± 3 |
5000 |
3 ± 1 |
0 ± 0 |
3 ± 1 |
0 ± 0 |
1 ± 2 |
Positive control |
115 ± 12 |
551 ± 8 |
272 ± 6 |
644 ± 121 |
117 ± 7 |
In the presence of metabolic activation |
|||||
Vehicle control |
20 ± 2 |
151 ± 15 |
17 ± 5 |
6 ± 2 |
20 ± 6 |
75 |
22 ± 5 |
163 ± 20 |
17 ± 2 |
5 ± 1 |
19 ± 6 |
200 |
18 ± 5 |
168 ± 6 |
19 ± 2 |
6 ± 2 |
16 ± 2 |
600 |
22 ± 3 |
154 ± 6 |
21 ± 4 |
6 ± 3 |
16 ± 3 |
1800 |
22 ± 2 |
144 ± 11 |
23 ± 2 |
6 ± 2 |
9 ± 3 |
5000 |
4 ± 2 |
0 ± 0 |
6 ± 2 |
0 ± 0 |
0 ± 0 |
Positive control |
1000 ± 147 |
74 ± 74 |
108 ± 9 |
128 ± 17 |
794 ± 95 |
Applicant's summary and conclusion
- Conclusions:
- Mixed xylenols were found to be negative for genotoxicity.
- Executive summary:
All criteria for a valid study were met. The results indicate that mixed xylenols did not cause a positive response either in the presence or absence of metabolic activation by Aroclor-induced rat liver S9. Mixed xylenols were therefore concluded to be negative for genotoxicity.
The above results are suitable to be used for read across for Reaction mass of 2,4-xylenol and 2,5-xylenol, due to the category being based on structural similarity and comparable physicochemical properties, leading to similar (eco)toxicological properties.
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