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EC number: 604-263-8 | CAS number: 14192-26-8
- 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
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Study period:
- Jan 29 - Feb 01, 2002
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- other: study well documented, meets generally accepted scientific principles, acceptable for assessment
Data source
Reference
- Reference Type:
- study report
- Title:
- Unnamed
- Year:
- 2 002
- Report date:
- 2002
Materials and methods
Test guideline
- Guideline:
- other: instruction manual for the Ames II (Xenometrix, Boulder/USA)
- Principles of method if other than guideline:
- The chemical intermediate BIBF 1120/CDBC 0167 XX, a chemical intermediate of the BIBF 1120 ES - synthesis was investigated in a modified bacterial mutagenicity test as described by Ames et al. (1975). This high throughput microtiter-based version, called Ames II, is based on the same genetic principle (base-pair substitution and frameshift mutations in the his operon of S. typhimurium) as a traditional Ames I assay combined with the fluctuation method (Gee et al., 1998).
- GLP compliance:
- no
- Type of assay:
- bacterial reverse mutation assay
Test material
- Reference substance name:
- methyl 2-oxo-2,3-dihydro-1H-indole-6-carboxylate
- EC Number:
- 604-263-8
- Cas Number:
- 14192-26-8
- Molecular formula:
- C10 H9 N O3
- IUPAC Name:
- methyl 2-oxo-2,3-dihydro-1H-indole-6-carboxylate
- Test material form:
- solid: particulate/powder
Constituent 1
Method
Species / strain
- Species / strain / cell type:
- S. typhimurium, other: TA 7001 - 7006 and TA 98
- Metabolic activation:
- with and without
- Metabolic activation system:
- S9 mix
- Test concentrations with justification for top dose:
- 1 to 5000 µg/ml (7 concentration levels: 1, 4, 20, 100, 500, 2500, 5000µg/ml)
- Vehicle / solvent:
- - Vehicle(s)/solvent(s) used: DMSO
Controls
- Untreated negative controls:
- no
- Negative solvent / vehicle controls:
- yes
- True negative controls:
- no
- Positive controls:
- yes
- Positive control substance:
- 4-nitroquinoline-N-oxide
- 2-nitrofluorene
- other: 2-aminoanthracene
- Details on test system and experimental conditions:
- Test Design
The Ames II test was conducted in presence and absence of a metabolic activation system (S9mix: microsomalliver enzymes from rats, Aroclor 1254-induced and co-factors). Following base-pair and frameshift-specific tester strains were used: S. typhimurium TA Mix (TA7001, TA 7002, TA 7003, TA 7004, TA 7005 and TA 7006) and TA 98, respectively. The Salmonella strains were described by Gee et al. (1998).
Techniques
The assay was performed according to the instruction manual for the Ames II (Xenometrix,
Boulder/USA). 0.01 ml ofthe vehicle, test article or positive control were incubated with
0.24 ml bacterial ovemight culture (ca 107/ml)/exposure medium in 24-well plates for 90 min
at 37°C and 250 rpm. With metabolic activation 0.2 ml strain mixture and 0.04 ml S9-mix
(30%) were used. After 90 min the exposed cultures were diluted with pH indicator medium
lacking histidine and aliquoted into 48 wells of a 384-well plate (3 replicates) using a 8-
channel pipettor. The plates were incubated for 48 hrs at 37°C. - Rationale for test conditions:
- The experiment is regarded valid, if the vehicle control showed the normal spontaneous revertant
frequency and the diagnostic mutagens caused the expected increase in the mutation rate. The individual test chemicals were classified according to the following criteria:
Negative: <=8/48 wells Equivocal: 9-12/48 wells Positive: >=13/48 wells
Our historical control range: 0-7/48 wells
A concentration-dependent increase of revertant wells (mean of triplicate) over the vehicle control is indicative of genotoxic activity. - Evaluation criteria:
- The pH indicator bromocresol purple tums the colour ofthe cultures from blue to yellow as
the pH drops due to the accumulation of catabolites from the metabolic activity of revertant
cells. The number of positive wells (yellow) out of a total of 48 wells is an indication of the
frequency of reversion per replicate per dose and was compared to the number of spontaneaus
revertant wells ofthe vehicle control. Each test point contains 48 wells of a 384-well plate. In
each 48-well section, the wells were scored for the number ofrevertant wells (yellow) and the
mean value of the triplicates was calculated.
Results and discussion
Test results
- Species / strain:
- other: S. typhimurium TA (7001, 7002, 7003, 7004, 7005, 7006 and TA 98
- Metabolic activation:
- with and without
- Genotoxicity:
- negative
- Cytotoxicity / choice of top concentrations:
- no cytotoxicity, but tested up to precipitating concentrations
- Vehicle controls validity:
- valid
- Untreated negative controls validity:
- not examined
- Positive controls validity:
- valid
- Additional information on results:
- BIBF 1120 Indol precipitated at concentrations of >= 2500 μg/ml following the incubation
for 90 min at 37 °C. Bacteriotoxicity, as seen by a reduced background lawn, was
observed at concentrations of >= 2500 μg/ml only in the absence of S9 mix.
Applicant's summary and conclusion
- Conclusions:
- Based on the described results it is concluded, that BIBF 1120 Indol when tested up to maximum recommended concentrations, caused neither base-pair substitution nor frameshift mutations in bacteria. No evidence of genotoxic activity was observed in a series of S. typhimurium tester strains (TA mix and TA 98) in the absence and presence of metabolic activation. The test compounds are, therefore, classified as "Ames II negative".
- Executive summary:
BIBF 1120 Indol was tested whether it induces mutations inS. typhimurium TA Mix (TA 7001, TA 7002, TA 7003, TA 7004, TA 7005, TA 7006 sensitive to base-pair substitution) and TA 98 (susceptible to frameshift mutagens) bacterial tester strains. BIBF 1120/CDBC 0167 XX was dissolved in dimethylsulfoxide (DMSO) and added to bacterial suspensionsbothin presence and absence of a metabolic activation system (S9 mix: rat liver preparation and co-factors) to give final concentrations ranging from 1 to 5000 flg/ml. The bacteria were transferred to 384-well plates after 90 minutes incubation at 37°C and further incubated for 48 hours at 37°C when revertant growth was quantified colorimetrically.
BIBF 1120 Indol precipitated at concentrations of >/= 2500 μg/ml following the incubation for 90 min at 37 °C. Bacteriotoxicity, as seen by a reduced background lawn, was observed at concentrations of >/= 2500 μg/ml only in the absence of S9 mix.
BIBF 1120 Indol did not consistently increase the number of positive (revertant)
wells in the different tester strains compared to the vehicle control neither in presence nor
absence of S9mix. The number ofrevertants from the vehicle and positive controls remained
within the range of our historical controls showing the validity of the study.
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