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EC number: 205-575-3 | CAS number: 142-96-1
- 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:
- 1992
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- test procedure in accordance with generally accepted scientific standards and described in sufficient detail
- Remarks:
- Standard Guideline study according to GLP: The test has been performed according to the old OECD TG 471 (1983) requiring the four Salmonella typhimurium strains used. The adopted OECD TG 471 (1997) requires the additional use of E. coli WP2 strains or Salmonella thyphimurium TA102 to detect certain oxidising mutagens, cross-linking agents and hydrazines. However, dibutyl ether is not a highly reactive agent and is therefore not expected to be a cross-linking agent, has no oxidising properties and is no hydrazine. Thus a GLP test according to OECD TG 471 (1983) without E. coli WP2 strains or Salmonella typhimurium TA102 is considered as sufficient to evaluate the mutagenic activity of dibutyl ether in this bacterial test system.
Data source
Reference
- Reference Type:
- publication
- Title:
- Salmonella mutagenicity test: V. Results from testing of 311 chemicals
- Author:
- Zeiger, E., Anderson, B., Haworth, S., Lawlor, T., Mortelmans, K.
- Year:
- 1 992
- Bibliographic source:
- Environ. Molecular Mutagen., 19, Suppl. 21, 2-141
Materials and methods
Test guideline
- Qualifier:
- equivalent or similar to guideline
- Guideline:
- OECD Guideline 471 (Bacterial Reverse Mutation Assay)
- Deviations:
- not specified
- Principles of method if other than guideline:
- Method: other: according to Haworth et al. (1983) with minor variations
- GLP compliance:
- not specified
- Type of assay:
- bacterial reverse mutation assay
Test material
- Reference substance name:
- Dibutyl ether
- EC Number:
- 205-575-3
- EC Name:
- Dibutyl ether
- Cas Number:
- 142-96-1
- Molecular formula:
- C8H18O
- IUPAC Name:
- 1-butoxybutane
- Details on test material:
- dibutyl ether (purity > 99 %)
Constituent 1
Method
- Target gene:
- not applicable
Species / strain
- Species / strain / cell type:
- S. typhimurium TA 1535, TA 1537, TA 98 and TA 100
- Details on mammalian cell type (if applicable):
- no data
- Additional strain / cell type characteristics:
- not specified
- Metabolic activation:
- with and without
- Metabolic activation system:
- S9
- Test concentrations with justification for top dose:
- 3.3-667 µg/plate
- Vehicle / solvent:
- 95% ethanol
Controls
- Untreated negative controls:
- not specified
- Negative solvent / vehicle controls:
- yes
- True negative controls:
- no
- Positive controls:
- yes
- Positive control substance:
- other: sodium azide, 9-aminoacridine, 4-nitro-o-phenylenediamine, 2-aminoanthracene
- Details on test system and experimental conditions:
- The Ames test was performed as preincubation test in the absence of exogenous metabolic activation and in the presence of liver S-9 fractions of Aroclor 1254-induced male Sprague-Dawley rats and male Syrian hamsters. An initial toxicity assay to determine the appropriate concentration range for the mutagenicity assay was run. Toxic concentrations were defined as those that produced a decrease in the number of the his+ colonies, or a clearing in the density of the background lawn, or both. In the mutagenicity assay 5 concentrations per test variation were tested in triplicate, and repeat experiments were performed at least one weak following the initial trial. Concurrent solvent (95% ethanol) and positive controls were run with each trial. Positive control substances were in the trials without metabolic activation sodium azide for TA1535 and TA100, 9-aminoacridine for TA97, and 4-nitro-o-phenylenediamine for TA98, and in the trials with metabolic activation 2-aminoanthracene for all strains.
- Evaluation criteria:
- A chemical was designated nonmutagenic only after it had been tested in all strains without activation, and with 10% and 30% rat and hamster S-9. A chemical was judged mutagenic or weakly mutagenic if it produced a reproducible, dose-related response over the solvent control, under a single metabolic activation condition, in replicate trials.
Results and discussion
Test resultsopen allclose all
- Key result
- Species / strain:
- E. coli WP2 uvr A
- Remarks:
- The adopted OECD TG 471 (1997) requires the additional use of E. coli WP2 strains or Salmonella thyphimurium TA102 to detect certain oxidising mutagens, cross-linking agents and hydrazines. However, dibutyl ether is not a highly reactive agent and is ther
- Metabolic activation:
- not applicable
- Genotoxicity:
- not determined
- Cytotoxicity / choice of top concentrations:
- not determined
- Untreated negative controls validity:
- not applicable
- True negative controls validity:
- not applicable
- Positive controls validity:
- not applicable
- Key result
- Species / strain:
- S. typhimurium TA 1535
- Metabolic activation:
- with and without
- Genotoxicity:
- negative
- Cytotoxicity / choice of top concentrations:
- other: >/= 100 µg/plate
- Vehicle controls validity:
- valid
- Untreated negative controls validity:
- valid
- Positive controls validity:
- valid
- Key result
- Species / strain:
- S. typhimurium TA 1537
- Metabolic activation:
- with and without
- Genotoxicity:
- negative
- Cytotoxicity / choice of top concentrations:
- other: >/= 100 µg/plate
- Vehicle controls validity:
- valid
- Untreated negative controls validity:
- valid
- Positive controls validity:
- valid
- Key result
- Species / strain:
- S. typhimurium TA 98
- Metabolic activation:
- with and without
- Genotoxicity:
- negative
- Cytotoxicity / choice of top concentrations:
- other: >/= 100 µg/plate
- Vehicle controls validity:
- valid
- Untreated negative controls validity:
- valid
- Positive controls validity:
- valid
- Key result
- Species / strain:
- S. typhimurium TA 100
- Metabolic activation:
- with and without
- Genotoxicity:
- negative
- Cytotoxicity / choice of top concentrations:
- other: >/= 100 µg/plate
- Vehicle controls validity:
- valid
- Untreated negative controls validity:
- valid
- Positive controls validity:
- valid
- Additional information on results:
- No test was conducted with E. Coli WP2
Any other information on results incl. tables
None
Applicant's summary and conclusion
- Conclusions:
- Interpretation of results (migrated information): negative
Dibutyl ether did not produce an dose-dependent increase of the number of his+ revertants/plate in the Salmonella typhimurium strains used neither in the absence nor in the presence of a metabolic activation system. Dose selection appears to be in a suitable range, because a bacteriotoxic effect was observed at the highest dose or the two highest doses tested (without metabolic activation 100 and/or 200 µg/plate with all strains; with metabolic activation depending on bacterial strain, kind and amount of liver S-9 fractions 100, 333, 334, 666 and/or 667 µg/plate). In each test well proven positive controls produced mutagenic effects demonstrating the functionally of the test system. - Executive summary:
In this study, the Ames test was performed as preincubation test in the absence of exogenous metabolic activation and in the presence of liver S-9 fractions of Aroclor 1254-induced male Sprague-Dawley rats and male Syrian hamsters. An initial toxicity assay to determine the appropriate concentration range for the mutagenicity assay was run. Toxic concentrations were defined as those that produced a decrease in the number of the his+ colonies, or a clearing in the density of the background lawn, or both. In the mutagenicity assay 5 concentrations per test variation were tested in triplicate, and repeat experiments were performed at least one weak following the initial trial. Concurrent solvent (95% ethanol) and positive controls were run with each trial. Positive control substances were in the trials without metabolic activation sodium azide for TA1535 and TA100, 9-aminoacridine for TA97, and 4-nitro-o-phenylenediamine for TA98, and in the trials with metabolic activation 2-aminoanthracene for all strains.
Dibutyl ether did not produce an dose-dependent increase of the number of his+ revertants/plate in the Salmonella typhimurium strains used neither in the absence nor in the presence of a metabolic activation system. Dose selection appears to be in a suitable range, because a bacteriotoxic effect was observed at the highest dose or the two highest doses tested (without metabolic activation 100 and/or 200 µg/plate with all strains; with metabolic activation depending on bacterial strain, kind and amount of liver S-9 fractions 100, 333, 334, 666 and/or 667 µg/plate). In each test well proven positive controls produced mutagenic effects demonstrating the functionally of the test system
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