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EC number: 252-200-4 | CAS number: 34762-90-8
- 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 mammalian cells
- Remarks:
- Type of genotoxicity: gene mutation
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Study period:
- 13 June 2014 to 14 July 2014.
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- other: GLP Guideline study.
Data source
Reference
- Reference Type:
- study report
- Title:
- Unnamed
- Year:
- 2 014
- Report date:
- 2014
Materials and methods
Test guideline
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 476 (In Vitro Mammalian Cell Gene Mutation Test)
- Deviations:
- no
- GLP compliance:
- yes (incl. QA statement)
- Type of assay:
- mammalian cell gene mutation assay
Test material
- Reference substance name:
- Trichloro(N,N-dimethyloctylamine)boron
- EC Number:
- 252-200-4
- EC Name:
- Trichloro(N,N-dimethyloctylamine)boron
- Cas Number:
- 34762-90-8
- Molecular formula:
- C10H23BCl3N
- IUPAC Name:
- dimethyl(octyl)(trichloro-λ⁵-boranylidene)amine
- Test material form:
- other: Solid
- Details on test material:
- - Test Substance I.D.: (TK 12146)
- Test Substance Lot Number: AEC0123100
- Test Substance Purity: 99% (provided by Sponsor)
- Test Substance Description: Amber solid
- Storage Conditions: Room temperature, protected from light
- Test Substance Receipt/Login Date: 28 May 2014
Constituent 1
Method
- Target gene:
- Evaluation the test substance for its ability to induce forward mutations at the hypoxanthine-guanine phosphoribosyl transferase (1-IPRT) locus (hprt) of Chinese Hamster Ovary (CHO) cells, in the presence and absence of an exogenous metabolic activation system (S9), as assayed by colony growth in the presence of 6-thioguanine (TG resistance, TG').
Species / strain
- Species / strain / cell type:
- Chinese hamster Ovary (CHO)
- Additional strain / cell type characteristics:
- not applicable
- Metabolic activation:
- with and without
- Metabolic activation system:
- Aroclor 1254-induced rat liver S9 .
- Test concentrations with justification for top dose:
- TK 12146 was prepared in DMSO and evaluated in a preliminary toxicity assay at concentrations of 10.7, 21.4, 42.8, 85.6, 171, 343, 685, 1370 and 2740 microg/mL with and without S9 (the maximum concentration evaluated approximated the I0 mM limit dose for this assay).
Based on these results, TK 12146 was evaluated in the definitive mutagenicity assay at concentrations of 6.25, 12.5, 25.0, 50.0, 100 and 200 microg/mL with and without S9. - Vehicle / solvent:
- The vehicle used to deliver TK 12146 to the test system was DMSO (CAS No. 67-68-5; Lot No. Sl-IBC3749V, Pmity: 99.92%, Expiration Date: April
2016), obtained fi·om Sigma-Aldrich.
Controls
- Untreated negative controls:
- yes
- Negative solvent / vehicle controls:
- yes
- Remarks:
- DMSO (Dimethylsulfoxide)
- True negative controls:
- no
- Positive controls:
- yes
- Positive control substance:
- methylmethanesulfonate
- other: Benzo(a)pyrene
- Remarks:
- Both were prepared at the appropriate concentration in DMSO
- Evaluation criteria:
- A test substance was considered to have induced a positive response if there was a concentration-related increase in mutant fi·equency with at least two consecutive doses showing mutant frequencies of>40 mutants per 10E6 clonable cells. If a single point above 40 mutants per I 06 clonable cells was observed at the highest dose, the results were considered equivocal. If no culture exhibited a mutant frequency of >40 mutants per 10E6 clonable cells, the test
substance was considered negative.
Other criteria also may be used in reaching a conclusion about the study results (e.g., comparison to historical control values, biological significance, etc.). In such cases, the Study Director used sound scientific judgment and clearly reported and described any such considerations. - Statistics:
- The primary computer or electronic systems used for the collection of data or analysis included but were not limited to the following:
- LIMS Labware System: Test Substance tracking
- Excel (Microsoft Corporation): Calculations
- Kaye Lab Watch Monitoring system (Kaye GE): Environmental monitoring
- BRIQS: Deviation and audit repmting
- ProtoCOL Colony Counter: Data collection
Results and discussion
Test results
- Species / strain:
- Chinese hamster Ovary (CHO)
- Metabolic activation:
- with and without
- Genotoxicity:
- negative
- Cytotoxicity / choice of top concentrations:
- no cytotoxicity
- Vehicle controls validity:
- valid
- Untreated negative controls validity:
- not applicable
- 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
Solubility Test
DMSO was selected as the solvent of choice based on the solubility of the test substance and compatibility with the target cells. The test substance formed a clear solution in DMSO at a concentration of approx.500 mg/mL, the maximum tested.
Preliminary Toxicity Assay
Results of the preliminary toxicity assay are presented in Table I. TK 12146 was prepared in DMSO and evaluated in a preliminary toxicity assay at concentrations of I 0.7, 21.4, 42.8, 85.6, 171, 343, 685, 1370 and 2740 microg/mL with and without S9 (the maximum concentration evaluated approximated the 10 mM limit dose for this assay). Visible precipitate was observed at concentrations >=85.6 microg/mL at the beginning and end of treatment. The test substance did not have an adverse impact on the pH or osmolality of the cultures (437 and 431 mmol/kg for the solvent control and 42.8 f!g/mL, the highest soluble concentration at the
beginning of treatment, respectively). Relative survival was 112.10 and 84.58% at a concentration of 2740 microg/mL with and without S9, respectively.
Definitive Mutagenicity Assay
Results of the mutagenicity assay are presented in Table 2. Based on the results of the preliminary toxicity assay, TK 12146 was evaluated in the definitive mutagenicity assay at concentrations of 6.25, 12.5, 25.0, 50.0, 100 and 200 microg/mL with and without S9. Visible precipitate was observed at concentrations 2:50.0 microg/mL at the beginning and end of treatment.Cultures treated at concentrations of6.25, 12.5, 25.0, 50.0 and 100 microg/mL with and without S9 were chosen for mutant selection (cultures treated at 200 pg/mL were discarded prior to selection because the limit of solubility was reached). The average relative survival was 85.47
and I 03.79% at a concentration of I 00 pg/mL with and without S9, respectively. No increases in average mutant frequency >40 mutants per I10E6 were observed at any concentration evaluated with or without S9.
All positive and vehicle control values were within acceptable ranges, and all criteria for a valid assay were met.
Applicant's summary and conclusion
- Conclusions:
- Under study conditions, test substance was negative in the In vitro Mammalian Cell Forward Gene Mutation (CHO/HPRT) Assay.
- Executive summary:
An in vitro study was conducted to investigate the potential of test substance, trichloro(N,N-dimethyloctylamine) boron for its ability to induce forward mutations at the hypoxanthineguanine phosphoribosyl transferase (HPRT) locus (hprt) of Chinese hamster ovary (CHO) cells, according to OECD Guideline 476, in compliance with GLP in the presence and absence of an exogenous metabolic activation system (S9), as assayed by colony growth in the presence of6-thioguanine (TG resistance, TG'). Test substance was prepared in DMSO and evaluated in a preliminary toxicity assay at concentrations of 10.7, 21.4, 42.8, 85.6, 171, 343, 685, 1370 and 2740 micromL with and without S9 (the maximum concentration evaluated approximated the I0 mM limit dose for this assay). Visible precipitate was observed at concentrations 2:85.6 microg/mL at the beginning and end of treatment. The test substance did not have an adverse impact on the pH or osmolality of the cultures. Relative survival was 112.10 and 84.58% at a concentration of 2740 microg/mL with and without S9, respectively. Based on these results, test substance was evaluated in the definitive mutagenicity assay at concentrations of 6.25, 12.5, 25.0, 50.0, 100 and 200 microg/mL with and without S9. Visible precipitate was observed at concentrations >=50.0 microg/mL at the beginning and end of treatment. Cultures treated at concentrations of 6.25, 12.5, 25.0, 50.0 and 100 microg/mL with and without S9 were chosen for mutant selection (cultures treated at 200 microg/mL were discarded prior to selection because the limit of solubility was reached). The average relative survival was 85.47 and 103.79% at a concentration of 100 microg/mL with and without S9, respectively. Under study conditions, test substance was negative in the In vitro Mammalian Cell Forward Gene Mutation (CHO/HPRT) Assay (Stankowski, 2014).
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