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EC number: 292-429-7 | CAS number: 90622-29-0
- 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:
- migrated information: read-across based on grouping of substances (category approach)
- Adequacy of study:
- key study
- Study period:
- 2010-02-01 to 2010-02-12
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- other: This is a GLP guideline study and is used in read-across from Alchisor CAL 123 (see 'Read Across Justification Document'). The study merits a Klimisch 1 rating; Klimisch 2 when used for read-across.
Data source
Reference
- Reference Type:
- study report
- Title:
- Unnamed
- Year:
- 2 010
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:
- Alkenes, C11-12, hydroformylation products, distn. residues
- EC Number:
- 292-427-6
- EC Name:
- Alkenes, C11-12, hydroformylation products, distn. residues
- Cas Number:
- 90622-27-8
- Molecular formula:
- not available; UVCB
- IUPAC Name:
- Alkenes, C11-12, hydroformylation products, distn. residues
- Details on test material:
- - Name of test material (as cited in study report): Alkenes, C11-12, hydroformulation products, distn. residues
- Substance type: pure active substance
- Physical state: turbid colourless liquid
- Storage condition of test material: in the dark at ambient room temperature
Constituent 1
Method
Species / strain
- Species / strain / cell type:
- S. typhimurium TA 1535, TA 1537, TA 98, TA 100 and E. coli WP2
- Metabolic activation:
- with and without
- Metabolic activation system:
- S9 enzymes from the livers of Aroclor 1254-treated adult, male Fisher rats
- Test concentrations with justification for top dose:
- Toxicity test: 17 / 50 / 167 / 500 / 1667 / 5000 µg/plate
Main tests: 17 / 50 / 167 / 500 / 1667 / 5000 µg/plate - Vehicle / solvent:
- - Vehicle(s)/solvent(s) used: Acetone
- Justification for choice of solvent/vehicle: Initial solubility tests showed that acetone was a suitable solvent. Examination of the test item showed it to be a turbid liquid and it was normal for the suspended solid to separate from the liquid fraction at room temperature (confiremd by the Sponsor). The test item was thoroughly stirred before samples were taken for testing to ensure homogeneity. When the acetone was added, a clear, homogenous solution was obtained (both the solid and liquid components were fully in solution)
Controlsopen allclose all
- Untreated negative controls:
- no
- Negative solvent / vehicle controls:
- yes
- Remarks:
- DMSO
- True negative controls:
- no
- Positive controls:
- yes
- Positive control substance:
- other: Sodium azide, 1 µg/plate with S. typhimurium TA 1535 and TA100; 9-Aminoacridine, 80 µg/plate with S. typhimurium TA 1537; 2-Nitrofluorene, 1 µg/plate with S. typhimurium TA 98; N-Ethyl-N-nitro-N-nitrosoguanidine, 2 µg/plate with E. coli WP2uvrA
- Remarks:
- without metabolic activation
- Untreated negative controls:
- no
- Negative solvent / vehicle controls:
- yes
- Remarks:
- DMSO
- True negative controls:
- no
- Positive controls:
- yes
- Positive control substance:
- other: 2-Aminoanthracene, 2 µg/plate with S. typhimurium TA 1535 and TA 1537, 0.5 µg/plate with S. typhimurium TA 98 and TA 100, 20 µg/plate with E. coli WP2uvrA
- Remarks:
- with metabolic activation
- Details on test system and experimental conditions:
- METHOD OF APPLICATION: in agar (direct plate method) in the first test; pre-incubation in the second (repeat) test
DURATION
- Preincubation period: 20 min (only in the repeat test)
- Exposure duration: 2 days in the toxoicity test; 3 days in the mutation tests
NUMBER OF REPLICATIONS: 3
DETERMINATION OF CYTOTOXICITY:
- Method: Plates were microscopically examined for thinning of background lawn, condition of background lawn was assessed as normal, slightly thin lawn, thin lawn, very thin lawn or lawn absent.
OTHER EXAMINATIONS:
- The numbers of mutant colonies on each plate were determined using a Sorcerer Colony Counter (Perceptive Instruments) and captured electronically in a validated software system (Ames Study Manager, Perceptive Instruments), the plates were also examined microscopically for precipitates and for microcolony growth (condition of backgroun lawn was assessed as in the toxicity test).
- Quality control of bacterial strains: All bacterial strains were tested for ampicillin resistence, crystal violet and ultraviolett radiation sensitivity and for essential animo acid requirement.
OTHER:
To establish suitable exposure levels for the first mutation test an initial dose-finding test in the presence and absence of S9 mix with a single strain of bacteria, S. typhimurium TA 100 and one plate per exposure level was conducted (Toxicity test). - Evaluation criteria:
- Interpretation of mutagenicity:
- doubling of the mean concurrent vehicle control value for S. typhimurium strains TA 1535, TA 1537 and TA 98 and for E. coli WP2uvrA, resp. 1.5-fold increase over the control value for S. typhimurium strain TA 100
- if the mean colony count on the vehicle control plates was less than 10, then a value of 10 was assumed for assessment purposes (in such cases a minimum count of 20, representing a 2-fold increase over 10, was required before a response was registered)
- concentration-related response, at high concentration, this relationship may be reversed
- a response should be reproducible in the independent test
Acceptance criteria:
- each bacterial strain demonstrated typical responses to crystal violet, ampicillin and ultralviolet radiation
- at least 2 of the 3 vehicle control plates were within the historical vehicle control data
- at least 2-fold increases over the mean vehicle control values in at least 2 of the 3 positive control plates for each strain and activation state were obtained (in the case of TA 100, at least 1.5-fold was obtained)
- no toxicity or contamination was observed in at least 4 concentration levels
- in cases where a mutagenic response was observed, no more than one exposure level was discarded below the concentration that gave the highest mean colony number - Statistics:
- not performed
Results and discussion
Test resultsopen allclose all
- Species / strain:
- S. typhimurium TA 1535
- Metabolic activation:
- with and without
- Genotoxicity:
- negative
- Cytotoxicity / choice of top concentrations:
- cytotoxicity
- Remarks:
- slight toxicity was observed at the highest concentration of 5000 µg/plate
- Vehicle controls validity:
- valid
- Untreated negative controls validity:
- not examined
- Positive controls validity:
- valid
- Species / strain:
- S. typhimurium TA 1537
- Metabolic activation:
- with and without
- Genotoxicity:
- negative
- Cytotoxicity / choice of top concentrations:
- cytotoxicity
- Remarks:
- slight toxicity was observed at the highest concentration of 5000 µg/plate
- Vehicle controls validity:
- valid
- Untreated negative controls validity:
- not examined
- Positive controls validity:
- valid
- Species / strain:
- S. typhimurium TA 98
- Metabolic activation:
- with and without
- Genotoxicity:
- negative
- Cytotoxicity / choice of top concentrations:
- cytotoxicity
- Remarks:
- slight toxicity was observed at the highest concentration of 5000 µg/plate
- Vehicle controls validity:
- valid
- Untreated negative controls validity:
- not examined
- Positive controls validity:
- valid
- Species / strain:
- S. typhimurium TA 100
- Metabolic activation:
- with and without
- Genotoxicity:
- negative
- Cytotoxicity / choice of top concentrations:
- cytotoxicity
- Remarks:
- slight toxicity was observed at the highest concentration of 5000 µg/plate
- Vehicle controls validity:
- valid
- Untreated negative controls validity:
- not examined
- Positive controls validity:
- valid
- Species / strain:
- E. coli WP2 uvr A
- Metabolic activation:
- with and without
- Genotoxicity:
- negative
- Cytotoxicity / choice of top concentrations:
- cytotoxicity
- Vehicle controls validity:
- valid
- Untreated negative controls validity:
- not examined
- Positive controls validity:
- valid
- Additional information on results:
- TEST-SPECIFIC CONFOUNDING FACTORS
- Effects of pH: no data
- Effects of osmolality: no data
- Evaporation from medium: not applicable
- Water solubility: no data
- Precipitation: Precipitation at 1667 and 5000 µg/plate in both absence and presence of S9 mix.
- Other confounding effects: nothing mentioned
RANGE-FINDING/SCREENING STUDIES: Slight toxicity was observed as a thinning of the background lawn of microcolonies at the highest concentration in both the absence and the presence of S9 mix.
COMPARISON WITH HISTORICAL CONTROL DATA: The vehicle control values were within the normal/historical ranges recorded in the testing laboratory and reported in the literature with these strains of S. typhimurium and E. coli (Ames et al, 1975; Gatehouse et al, 1994). The positive control values were also within the normal/historical ranges for each bacterial strain and activation condition. - Remarks on result:
- other: all strains/cell types tested
- Remarks:
- Migrated from field 'Test system'.
Any other information on results incl. tables
Table #1: Toxicity test with S. typhimurium strain TA 100
without metabolic activation | with metabolic activation | |||
Dose level [µg/plate] | Revertant colony count | Ratio treated/solvent | Revertant colony count | Ration treated/solvent |
Acetone | 77 | - | 97 | - |
17 | 86 | 1.1 | 87 | 0.9 |
50 | 81 | 1.1 | 68 | 0.7 |
167 | 76 | 1.0 | 60 | 0.6 |
500 | 65 | 0.8 | 97 | 1.0 |
1667 | 76 P | 1.0 | 83 P | 0.9 |
5000 | 48 P ST | 0.6 | 57 P ST | 0.6 |
P = Precipitate / ST= Slightly Thin Lawn
Table #2: First Mutation Assay (Direct Plate Incorporation Method)
TA 1535 | TA 1537 | TA 98 | ||||||||||
- S9 mix | + S9 mix | - S9 mix | + S9 mix | - S9 mix | + S9 mix | |||||||
Dose level[µg/plate] | Mean revertants per plate ± SD | Ratio | Mean revertants per plate ± SD | Ratio | Mean revertants per plate ± SD | Ratio | Mean revertantsper plate± SD | Ratio | Mean revertants per plate ± SD | Ratio | Mean revertants per plate ± SD | Ratio |
Acetone | 14.0 ± 5.3 | - | 18.7 ± 4.0 | - | 10.0 ± 2.6 | - | 10.0 ± 2.6 | - | 40.0 ± 11.1 | - | 45.0 ± 6.6 | - |
17 | 13.0 ± 3.0 | 0.9 | 10.7 ± 1.2 | 0.6 | 5.7 ± 2.9 | 0.7 | 15.0 ± 5.0 | 1.5 | 32.0 ± 19.1 | 0.8 | 31.7 ± 3.2 | 0.7 |
50 | 12.7 ± 2.5 | 0.9 | 14.3 ± 3.1 | 0.8 | 7.0 ± 3.0 | 0.7 | 16.3 ± 3.5 | 1.6 | 23.3 ± 4.7 | 0.7 | 38.3 ± 5.5 | 0.9 |
167 | 15.3 ± 6.7 | 1.1 | 12.3 ± 4.6 | 0.7 | 11.0 ± 7.0 | 1.1 | 12.7 ± 1.5 | 1.3 | 31.3 ± 2.1 | 0.8 | 36.7 ± 12.9 | 0.8 |
500 | 7.0 ± 3.5 | 0.5 | 15.0 ± 0.0 | 0.8 | 8.3 ± 6.0 | 0.8 | 10.3 ± 2.9 | 1.0 | 36.3 ± 18.6 | 0.9 | 33.0 ± 8.2 | 0.7 |
1667 | 14.0 ± 4.4 P | 1.0 | 18.0 ± 1.0 P | 1.0 | 8.3 ± 2.1 P ST | 0.8 | 6.7 ± 2.5 P | 0.7 | 19.7 ± 3.2 P | 0.5 | 33.3 ± 5.5 P | 0.7 |
5000 | 13.0 ± 4.0 P ST | 0.9 | 16.0 ± 8.2 P | 0.9 | 10.3 ± 2.3 P TL | 1.0 | 7.3 ± 6.7 P ST | 0.9 | 20.0 ± 5.3 P ST | 1.0 | 33.7 ± 4.2 P ST | 0.7 |
Positive Control | 470.0 ± 31.0 | 33.6 | 592.0 ± 42.5 | 31.7 | 5809.3 ± 170.5 | 581 | 361.7 ± 16.8 | 36.2 | 607.0 ± 21.0 | 15.2 | 822.7 ± 58.2 | 18.3 |
P = Precipitate / ST= Slightly Thin Lawn / TL = Thin Lawn
Table #2 (continued): First Mutation Assay (Direct Plate Incorporation Method)
TA 100 | WP2uvrA | |||||||
- S9 mix | + S9 mix | - S9 mix | + S9 mix | |||||
Dose level [µg/plate] | Mean revertants per plate ± SD | Ratio | Mean revertants per plate ± SD | Ratio | Mean revertants per plate ± SD | Ratio | Mean revertants per plate ± SD | Ratio |
Acetone | 91.7 ± 11.4 | - | 101.3 ± 6.4 | - | 8.7 ± 1.5 | - | 13.0 ± 2.6 | - |
17 | 92.3 ± 7.4 | 1.0 | 88.0 ± 15.0 | 0.9 | 6.0 ± 2.6 | 0.7 | 10.7 ± 2.1 | 0.8 |
50 | 89.7 ± 8.5 | 1.0 | 98.3 ± 22.5 | 1.0 | 7.7 ± 1.2 | 0.9 | 9.3 ± 3.1 | 0.7 |
167 | 88.3 ± 5.0 | 1.0 | 79.7 ± 2.1 | 0.8 | 7.0 ± 0.0 | 0.8 | 8.0 ± 1.7 | 0.6 |
500 | 93.7 ± 8.1 | 1.0 | 88.3 ± 4.0 | 0.9 | 5.7 ± 3.5 | 0.7 | 7.3 ± 1.5 | 0.6 |
1667 | 80.0 ± 14.4 P | 0.9 | 86.3 ± 7.4 P | 0.9 | 7.0 ± 3.0 P | 0.8 | 8.7 ± 3.5 P | 0.7 |
5000 | 72.0 ± 3.6 P ST | 0.8 | 75.3 ± 3.1 P ST | 0.7 | 6.7 ± 1.2 P ST | 0.8 | 6.7 ± 3.1 P | 0.5 |
Positive control | 1059.0 ± 60.6 | 11.6 | 1130.0 ± 46.7 | 11.2 | 130.3 ± 24.8 | 15.0 | 469.3 ± 14.3 | 36.1 |
P = Precipitate / ST = Slightly Thin Lawn
Table #3: Second Mutation Assay (Pre-incubation Method)
TA 1535 | TA 1537 | TA 98 | ||||||||||
- S9 mix | + S9 mix | - S9 mix | + S9 mix | - S9 mix | + S9 mix | |||||||
Dose level [µg/plate] | Mean revertants per plate ± SD | Ratio | Mean revertants per plate ± SD | Ratio | Mean revertants per plate ± SD | Ratio | Mean revertantsper plate± SD | Ratio | Mean revertants per plate ± SD | Ratio | Mean revertants per plate ± SD | Ratio |
Acetone | 12.7 ± 3.5 | - | 17.3 ± 4.5 | - | 9.0 ± 2.6 | - | 19.0 ± 2.6 | - | 27.0 ± 4.6 | - | 35.0 ± 4.4 | - |
17 | 14.7 ± 8.5 | 1.2 | 18.3 ± 7.6 | 1.1 | 12.7 ± 2.1 | 1.4 | 20.7 ± 4.6 | 1.1 | 22.7 ± 8.5 | 0.8 | 37.7 ± 7.2 | 1.1 |
50 | 10.0 ± 1.0 | 0.8 | 12.7 ± 3.8 | 0.7 | 11.3 ± 2.1 | 1.3 | 20.0 ± 4.0 | 1.1 | 23.0 ± 5.0 | 0.9 | 39.7 ± 6.0 | 1.1 |
167 | 14.3 ± 5.1 | 1.1 | 14.3 ± 5.9 | 0.8 | 14.7 ± 4.6 | 1.6 | 16.0 ± 2.6 | 0.8 | 20.7 ± 1.2 | 0.8 | 33.0 ± 2.0 | 0.9 |
500 | 15.3 ± 4.9 | 1.2 | 18.0 ± 2.0 | 1.0 | 11.3 ± 2.1 | 1.3 | 12.7 ± 3.1 | 0.7 | 27.3 ± 9.0 | 1.0 | 31.7 ± 4.9 | 0.9 |
1667 | 13.7 ± 2.1P ST | 1.1 | 12.0 ± 5.6 P | 0.7 | 8.7 ± 4.0 P TL | 1.0 | 4.3 ± 2.1 P ST | 0.2 | 19.7 ± 3.2 P TL | 0.7 | 27.3 ± 4.0 P | 0.8 |
5000 | 10.7 ± 4.0 P TL | 0.8 | 13.3 ± 3.2 P ST | 0.8 | 5.3 ± 0.6 P TL | 0.6 | 9.0 ± 2.6 P TL | 0.5 | 24.5 P TL | 0.9 | 32.3 ± 9.8 P ST | 0.9 |
Positive Control | 525.0 ± 20.0 | 41.4 | 317.7 ± 13.7 | 18.3 | 4462.7 ± 423.7 | 496 | 179.0 ± 29.5 | 9.4 | 377.3 ± 28.1 | 14.0 | 177.7 ± 15.3 | 5.1 |
P = Precipitate / ST = Slightly Thin Lawn / TL = Thin Lawn
Table #3 (continued): Second Mutation Assay (Pre-incubation Method)
TA 100 | WP2uvrA | |||||||
- S9 mix | + S9 mix | - S9 mix | + S9 mix | |||||
Dose level [µg/plate] | Mean revertants per plate ± SD | Ratio | Mean revertants per plate ± SD | Ratio | Mean revertants per plate ± SD | Ratio | Mean revertants per plate ± SD | Ratio |
Acetone | 100.7 ± 10.5 | - | 95.7 ± 20.6 | - | 11.0 ± 1.7 | - | 9.7 ± 5.5 | - |
17 | 78.7 ± 16.2 | 0.8 | 78.7 ± 5.8 | 0.8 | 8.3 ± 6.1 | 0.8 | 7.3 ± 2.5 | 0.8 |
50 | 69.7 ± 4.7 | 0.7 | 94.3 ± 11.8 | 1.0 | 9.0 ± 3.6 | 0.8 | 6.3 ± 4.0 | 0.7 |
167 | 74.0 ± 19.1 | 0.7 | 100.3 ± 7.6 | 1.0 | 12.7 ± 3.5 | 1.2 | 3.3 ± 1.5 | 0.3 |
500 | 72.7 ± 5.0 | 0.7 | 88.0 ± 7.8 | 0.9 | 5.7 ± 0.6 | 0.5 | 5.7 ± 1.5 | 0.6 |
1667 | 73.7 ± 6.1 P VT | 0.7 | 85.3 ± 8.1 P | 0.9 | 2.7 ± 1.2 P TL | 0.2 | 5.3 ± 1.5 P | 0.6 |
5000 | 67.0 ± 7.0 P TL | 0.7 | 88.3 ± 4.5 P ST | 0.9 | 2.0 P VT | 0.2 | 8.0 ± 2.6 P | 0.8 |
Positive control | 1112.0 ± 33.5 | 11.0 | 570.7 ± 61.4 | 6.0 | 186.0 ± 36.5 | 16.9 | 242.3 ± 6.4 | 25.1 |
P = Precipitate / ST = Slightly Thin Lawn / TL = Thin Lawn / VT = Very Thin Lawn
Applicant's summary and conclusion
- Conclusions:
- Interpretation of results:
negative
No evidence of mutagenic activity was obtained with any strain in either test.
In the direct plate incorporation test, toxicity was encountered in all stains at the highest concentration or 2 highest concentrations in the absence of S9 mix and in 3 of 5 strains at the highest concentration in the presence of S9 mix. In the pre-incubation test, toxicity was encountered at the 2 highest concentrations in all strains in the absence of S9 mix, and in 4 of the 5 strains at the highest concentration or 2 highest concentrations in the presence of S9 mix. The test item precipitated at concentration s 1667 and 5000 µg/plate in all tests. In addition, the test substance precipitated at 1667 and 5000 µg/plate. - Executive summary:
Alkenes, C11 -12 hydroformulation products, distn. residues was tested for mutagenic activity in Salmonella typhimurium strains TA 1535, TA 1537, TA 98 and TA100 and in Escherichia coli WP2uvrA according to OECD guideline 471and the European Commision Annex V Test Method B13 and B14.
The test item was dissolved and diluted in Acetone. Two independent tests were conducted on agar plate in triplicate in the absence and presence of an Aroclor 1254 -induced rat liver S9 preparation and co-factors required for mixed function oxidase activity (S9 mix). The first test was conducted by the direct plate incorporation method, while the second test was conducted by the pre-incubation method. The test item was dosed at concentrations ranging from 17 to 5000 µg/plate in both assays. The highest concentration was the predetermined maximum, as recommended by relevant guidelines, but was in addition both toxic to the bacteria and above the limit of solubility of the tes item in the test system.
Concurrent positive controls demonstrated the sensitivity of the assay and the metabolising activity of the S9 mix.
No evidence of mutagenic activity was obtained with any strain in either test.
In the direct plate incorporation test, toxicity was encountered in all stains at the highest concentration or 2 highest concentrations in the absence of S9 mix and in 3 of 5 strains at the highest concentration in the presence of S9 mix. In the pre-incubation test, toxicity was encountered at the 2 highest concentrations in all strains in the absence of S9 mix, and in 4 of the 5 strains at the highest concentration or 2 highest concentrations in the presence of S9 mix. The test item precipitated at concentration s 1667 and 5000 µg/plate in all tests.
It was concluded that Alkenes, C11 -12, hydroformulation products, distn. residues was not mutagenic in strains of Salmonella typhimurium and Escherichia coli when tested in acetone in the absence and presence of metabolic activation. The test item was tested to the predetermined maximum of 5000 µg per plate, at which concentration toxicity was encountered. In addition, the test item was tested up to and beyond its limits of solubility in the test system.
The study was performed in accordance with the principles of Good Laboratory Practice.
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