Registration Dossier
Registration Dossier
Data platform availability banner - registered substances factsheets
Please be aware that this old REACH registration data factsheet is no longer maintained; it remains frozen as of 19th May 2023.
The new ECHA CHEM database has been released by ECHA, and it now contains all REACH registration data. There are more details on the transition of ECHA's published data to ECHA CHEM here.
Diss Factsheets
Use of this information is subject to copyright laws and may require the permission of the owner of the information, as described in the ECHA Legal Notice.
EC number: - | CAS number: -
- 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
Some information in this page has been claimed confidential.
Administrative data
- Endpoint:
- in vitro gene mutation study in bacteria
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- guideline study
Data source
Reference
- Reference Type:
- study report
- Title:
- Unnamed
- Year:
- 2 018
- Report date:
- 2018
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
- Test material form:
- semi-solid (amorphous): gel
Constituent 1
Results and discussion
Test resultsopen allclose all
- Key result
- Species / strain:
- S. typhimurium TA 100
- Metabolic activation:
- with and without
- Genotoxicity:
- negative
- Cytotoxicity / choice of top concentrations:
- no cytotoxicity
- Vehicle controls validity:
- valid
- Untreated negative controls validity:
- valid
- Positive controls validity:
- not valid
- Key result
- Species / strain:
- S. typhimurium TA 1537
- Metabolic activation:
- with and without
- Genotoxicity:
- negative
- Cytotoxicity / choice of top concentrations:
- no cytotoxicity
- Vehicle controls validity:
- valid
- Untreated negative controls validity:
- valid
- Positive controls validity:
- not applicable
- Key result
- Species / strain:
- E. coli WP2 uvr A
- Metabolic activation:
- with and without
- Genotoxicity:
- negative
- Cytotoxicity / choice of top concentrations:
- no cytotoxicity
- Vehicle controls validity:
- valid
- Untreated negative controls validity:
- valid
- Positive controls validity:
- not applicable
- Key result
- Species / strain:
- S. typhimurium TA 98
- Metabolic activation:
- with and without
- Genotoxicity:
- negative
- Cytotoxicity / choice of top concentrations:
- no cytotoxicity
- Vehicle controls validity:
- not valid
- Untreated negative controls validity:
- valid
- 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:
- no cytotoxicity
- Vehicle controls validity:
- valid
- Untreated negative controls validity:
- valid
- Positive controls validity:
- not applicable
Any other information on results incl. tables
In the first experiment, the maximum dose level of the test item was selected as 5000 μg/plate (the maximum recommended concentration) for all of the bacterial strains dosed in the presence of S9-mix (except TA100) and WP2uvrA dosed in the absence of S9-mix. Due to excessive test item toxicity, the toxic limit was set for all of the Salmonella bacterial tester strains dosed in the absence of S9-mix and TA100 dosed in the presence of S9-mix. The test item induced a visible reduction in the growth of the bacterial background lawns and/or substantial reductions in the revertant colony frequency of all of the Salmonella tester strains dosed in the absence of S9-mix from 50 μg/plate (TA100 and TA1537) and 150 μg/plate (TA1535 and TA98). Escherichia coli strain WP2uvrA exhibited substantial reductions in colony frequency at 5000 μg/plate. In the presence of S9-mix, weakened background lawns were initially noted from 150 μg/plate for Salmonella strains TA100 and TA1537 and 500 μg/plate for TA98 and TA1535. Escherichia coli strain WP2uvrA exhibited substantial reductions in colony frequency at 5000 μg/plate.
In the second experiment, the maximum recommended dose level or the toxic limit was employed as the maximum concentration, depending on bacterial strain type and absence or presence of S9-mix. The test item induced an identical toxic response to the first experiment with weakened bacterial background lawns initially noted at 50 μg/plate in both the presence and absence of S9-mix.
A test item precipitate was observed under a low power microscope at 1500 μg/plate and by eye at 5000 μg/plate, this observation did not prevent the scoring of revertant colonies.
There were no biologically relevant increases in the frequency of revertant colonies recorded for any of the bacterial strains, with any dose of the test item, either with or without metabolic activation (S9-mix) in Experiment 1. Similarly, no increases in the frequency of revertant colonies were recorded for any of the bacterial strains, with any dose of the test item, either with or without metabolic activation (S9-mix) in Experiment 2. A small statistical value was noted in Experiment 1 (WP2uvrA at 15 μg/plate in the presence of S9-mix), however this response was within the in-house historical vehicle/untreated control value for the strain and was, therefore considered of no biological relevance.
Applicant's summary and conclusion
- Conclusions:
- Test item was considered to be non-mutagenic under the conditions of this test.
- Executive summary:
1.1 Introduction
The test method was designed to be compatible with the guidelines for bacterial mutagenicity testing published by the major Japanese Regulatory Authorities including METI, MHLW and MAFF, the OECD Guidelines for Testing of Chemicals No. 471 "Bacterial Reverse Mutation Test", Method B13/14 of Commission Regulation (EC) number 440/2008 of 30 May 2008 and the USA, EPA OCSPP harmonized guideline - Bacterial Reverse Mutation Test.
1.2 Methods
Salmonella typhimurium strains TA1535, TA1537, TA98 and TA100 and Escherichia coli strain WP2uvrA were treated with the test item using the Ames plate incorporation method at up to eight dose levels, in triplicate, both with and without the addition of a rat liver homogenate metabolizing system (10% liver S9 in standard co-factors). The dose range for Experiment 1 was predetermined and was initially 1.5 to 5000 μg/plate. However, the test item exhibited excessive toxicity and consequently, there were an insufficient number of non-toxic dose levels for all of the Salmonella bacterial tester strains dosed in the absence of S9-mix and TA100 dosed in the presence of S9-mix. Therefore, these strains were repeated using an amended dose range of 0.05 to 150 μg/plate. Experiment 2 was perormed on a separate day using fresh cultures of the bacterial strains and fresh test item formulations. The dose range was amended following the results of Experiment 1 (and repeat) and ranged between 0.05 and 5000 μg/plate, depending on bacterial strain type and absence or presence of S9-mix. Up to eight test item concentrations per bacterial strain were selected in Experiment 2 in order to achieve four non-toxic dose levels.
1.3 Results
The vehicle (acetone) control plates gave counts of revertant colonies within the normal range. All of the positive control chemicals used in the test induced marked increases in the frequency of revertant colonies, both with or without metabolic activation. Thus, the sensitivity of the assay and the efficacy of the S9-mix were validated.
In the first experiment, the maximum dose level of the test item was selected as 5000 μg/plate (the maximum recommended concentration) for all of the bacterial strains dosed in the presence of S9-mix (except TA100) and WP2uvrA dosed in the absence of S9-mix. Due to excessive test item toxicity, the toxic limit was set for all of the Salmonella bacterial tester strains dosed in the absence of S9-mix and TA100 dosed in the presence of S9-mix. The test item induced a visible reduction in the growth of the bacterial background lawns and/or substantial reductions in the revertant colony frequency of all of the Salmonella tester strains dosed in the absence of S9-mix from 50 μg/plate (TA100 and TA1537) and 150 μg/plate (TA1535 and TA98). Escherichia coli strain WP2uvrA exhibited substantial reductions in colony frequency at 5000 μg/plate. In the presence of S9-mix, weakened background lawns were initially noted from 150 μg/plate for Salmonella strains TA100 and TA1537 and 500 μg/plate for TA98 and TA1535. Escherichia coli strain WP2uvrA exhibited substantial reductions in colony frequency at 5000 μg/plate.
In the second experiment, the maximum recommended dose level or the toxic limit was employed as the maximum concentration, depending on bacterial strain type and absence or presence of S9-mix. The test item induced an identical toxic response to the first experiment with weakened bacterial background lawns initially noted at 50 μg/plate in both the presence and absence of S9-mix.
A test item precipitate was observed under a low power microscope at 1500 μg/plate and by eye at 5000 μg/plate, this observation did not prevent the scoring of revertant colonies.
There were no biologically relevant increases in the frequency of revertant colonies recorded for any of the bacterial strains, with any dose of the test item, either with or without metabolic activation (S9-mix) in Experiment 1. Similarly, no increases in the frequency of revertant colonies were recorded for any of the bacterial strains, with any dose of the test item, either with or without metabolic activation (S9-mix) in Experiment 2. A small statistical value was noted in Experiment 1 (WP2uvrA at 15 μg/plate in the presence of S9-mix), however this response was within the in-house historical vehicle/untreated control value for the strain and was, therefore considered of no biological relevance.
Information on Registered Substances comes from registration dossiers which have been assigned a registration number. The assignment of a registration number does however not guarantee that the information in the dossier is correct or that the dossier is compliant with Regulation (EC) No 1907/2006 (the REACH Regulation). This information has not been reviewed or verified by the Agency or any other authority. The content is subject to change without prior notice.
Reproduction or further distribution of this information may be subject to copyright protection. Use of the information without obtaining the permission from the owner(s) of the respective information might violate the rights of the owner.
Although ECHA is providing a lot of online material in your language, part of this page is only in English. More about ECHA’s multilingual practice.
Welcome to the ECHA website. This site is not fully supported in Internet Explorer 7 (and earlier versions). Please upgrade your Internet Explorer to a newer version.
the-echa-website-uses-cookies
find-out-more-on how-we-use-cookies