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EC number: 203-445-0 | CAS number: 106-94-5
- 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:
- experimental study
- Adequacy of study:
- key study
- Study period:
- 27th October - 10th December 1993
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- other: Study conducted to GLP in compliance with agreed protocols, with no or minor deviations from standard test guidelines and/or minor methodological deficiencies, which do not affect the quality of the relevant results.
Data source
Reference
- Reference Type:
- study report
- Title:
- Unnamed
- Year:
- 1 993
- Report date:
- 1994
Materials and methods
Test guideline
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 471 (Bacterial Reverse Mutation Assay)
- Deviations:
- no
- GLP compliance:
- yes (incl. QA statement)
- Type of assay:
- bacterial reverse mutation assay
Test material
- Reference substance name:
- 1-bromopropane
- EC Number:
- 203-445-0
- EC Name:
- 1-bromopropane
- Cas Number:
- 106-94-5
- Molecular formula:
- CH3CH2CH2Br
- IUPAC Name:
- 1-bromopropane
- Details on test material:
- > 99%
Constituent 1
Method
- Target gene:
- Histidine
Species / strain
- Species / strain / cell type:
- other: S. typhimurium TA 1535, TA 1537, TA 1538, TA 98 and TA 100
- Details on mammalian cell type (if applicable):
- n/a
- Additional strain / cell type characteristics:
- other: See any other information on materials and methods section.
- Metabolic activation:
- with and without
- Metabolic activation system:
- S9 fraction from the livers of Aroclor 1254-induced Sprague Dawley rats
- Test concentrations with justification for top dose:
- 100, 500, 1000, 5000 and 10000 µg/plate
- Vehicle / solvent:
- DMSO (1%)
Controls
- Untreated negative controls:
- no
- Negative solvent / vehicle controls:
- yes
- True negative controls:
- no
- Positive controls:
- yes
- Positive control substance:
- other: See any other information on materials and methods.
- Details on test system and experimental conditions:
- METHOD OF APPLICATION: in agar (plate incorporation)
DURATION
- Preincubation period: 8 - 9 hours
- Exposure duration: 48 hours
- Expression time (cells in growth medium): N/A
- Selection time (if incubation with a selection agent): N/A
- Fixation time (start of exposure up to fixation or harvest of cells): N/A
SELECTION AGENT (mutation assays): NDA
SPINDLE INHIBITOR (cytogenetic assays): NDA
STAIN (for cytogenetic assays): NDA
NUMBER OF REPLICATIONS: 3
DETERMINATION OF CYTOTOXICITY
- Method: bacterial lawn
- Evaluation criteria:
- Evaluation of Toxicity:
The compound induced toxicity was evaluated on every plate at the end of the incubation period by studying the aspect of the bacterial lawn and the number of His+ revertant colonies/plate
The bacterial background lawn is examined folowing the criteria listed below:
- Normal background lawn
+ Partial sparsity of background lawn (microscopic observation, lens 10 x 10)
++ Sparsity of background lawn (macroscopic observation)
+++ Inhibition of background lawn or presence of background lawn colonies
Evaluation of Genotoxicity:
The revertant colonies were counted using an AMS counter or with the naked eye when there was less than 20 of them.
The results are expressed as the number of His+ revertant colonies/plate. The following parameters were calculated for each concentration.
• the number of net revertants (mean number of His+ revertants colonies/plate less the mean number of spontaneous revertants colonies/plate for each concentration)
• the induction factor (ratio of the mean number of net revertant colonies/plate to the mean number of spontaneous revertant colonies/plate for each concentration).
A compound is considered genotoxic if:
• the number of His+ revertant colonies/plate at one concetration is at least twice the number of spontaneous revertants for TA98 and TA100 strains and three times this number for TA1535, TA 1537 and TA1538 strains
• the increase in the number of revertants is concentration related. - Statistics:
- NDA
Results and discussion
Test results
- Species / strain:
- other: S. typhimurium TA 1535, TA 1537, TA3538, TA 98 and TA 100
- Metabolic activation:
- with and without
- Genotoxicity:
- negative
- Cytotoxicity / choice of top concentrations:
- cytotoxicity
- Remarks:
- seen at 5000 µg/plate and above.
- Vehicle controls validity:
- valid
- Untreated negative controls validity:
- not examined
- Positive controls validity:
- valid
- Additional information on results:
- RANGE-FINDING/SCREENING STUDIES:
In the preliminary study using TA1535 annd TA100 without activation, cytotoxocity was seen at 10,000 ug/plate and this was therefore maintained as the highest concentration for the definitive study.
ADDITIONAL INFORMATION ON CYTOTOXICITY:
A slight toxic effect (sparsity of the background lawn with or without a decrease in the number of reverant colonies/plate) was noted at 5000 and 10,000 µg/plate for plates with metabolic activation and at 10,000 µg/plate without metabolic activation.
ADDITIONAL INFORMATION ON GENOTOXICITY:
No genetic toxicity was induced at any concentration with any of the tester strains. Genotoxocity was shown with the positive control substances showing the validity of the test system. A second study was conducted with the same concentrations and same tester strains as the first and produced results in agreement with the original definitive study. - Remarks on result:
- other: strain/cell type:
- Remarks:
- Migrated from field 'Test system'.
Applicant's summary and conclusion
- Conclusions:
- Interpretation of results (migrated information):
negative
The genotoxic potential of n-propyl bromide was assessed by the Ames test on five Salmonella typhimurium tester strains: TA1353, TA1537, TA1538, TA98 and TA100, both in the absence and presence of metabolic activation.
n-propyl bromide was dissolved and diluted in dimethyl sulfoxide and tested at concentrations ranging from 100 to 10,000 µg/plate.
During the first genotoxicity study (HIS1005) performed at 100, 500, 1000, 5000 and 10,000 µg/plate, a slight toxic affect was observed mainly at 10,000 µg/plate on the five tester strains with S9 mux and in TA1535, TA 1538, TA98 and TA100 without S9 mix.
A second study (HIS1005A) performed at the same concentrations confirmed these results.
In both studies, whether in the presence or in the absence of metabolic activation, no increase was observed in the number of His+ revertant colonies/plate at any of the concentrations tested, on the five tester strains, with and without S9 mix.
In conclusion, n-propyl bromide was not genotoxic in the Ames test, with or without metabolic activation. - Executive summary:
The genotoxic potential of n-propyl bromide was assessed by the Ames test on five Salmonella typhimurium tester strains: TA1353, TA1537, TA1538, TA98 and TA100, both in the absence and presence of metabolic activation.
n-propyl bromide was dissolved and diluted in dimethyl sulfoxide and tested at concentrations ranging from 100 to 10,000 µg/plate.
During the first genotoxicity study (HIS1005) performed at 100, 500, 1000, 5000 and 10,000 µg/plate, a slight toxic effect was observed mainly at 10,000 µg/plate on the five tester strains with S9 mux and in TA1535, TA 1538, TA98 and TA100 without S9 mix.
A second study (HIS1005A) performed at the same concentrations confirmed these results.
In both studies, whether in the presence or in the absence of metabolic activation, no increase was observed in the number of His+ revertant colonies/plate at any of the concentrations tested, on the five tester strains, with and without S9 mix.
In conclusion, n-propyl bromide was not genotoxic in the Ames test, with or without metabolic activation.
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