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EC number: 240-211-7 | CAS number: 16066-38-9
- 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
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Endpoint summary
Administrative data
Key value for chemical safety assessment
Genetic toxicity in vitro
Description of key information
The potential of LUPEROX 221 to induce reverse mutations was evaluated inSalmonella typhimurium (Brient, 2016). The study was performed according to the international guidelines and in compliance with the principles of Good Laboratory Practice. A preliminary toxicity test was performed to define the dose-levels of LUPEROX 221, dissolved in ethanol, to be used for the mutagenicity experiments. The test item was then tested in two independent experiments, both with and without a metabolic activation system, the S9 mix, prepared from a liver post-mitochondrial fraction (S9 fraction) of rats induced with Aroclor 1254. Treatments were performed according to the direct plate incorporation method except for the second experiment with S9 mix, which was performed according to the pre-incubation method (60 minutes, 37°C). Five strains of bacteriaSalmonella typhimuriumwere used: TA 1535, TA 1537, TA 98, TA 100 and TA 102. Each strain was exposed to six dose-levels of the test item (three plates/dose-level). After 48 to 72 hours of incubation at, the revertant colonies were scored. The evaluation of the toxicity was performed on the basis of the observation of the decrease in the number of revertant colonies and/or a thinning of the bacterial lawn.
According to available solubility data, the test item was found to be freely soluble in the vehicle at the concentration of 200 mg/mL. Consequently, using a maximum treatment-volume of 25 µL/plate, the dose-levels used for the preliminary toxicity test were 10, 100, 500, 1000, 2500 and 5000 µg/plate. No precipitate was observed in the Petri plates when scoring the revertants, at any of the tested dose-levels. A strong toxicity (thinning of the bacterial lawn and/or decrease in the number of revertants) was noted at dose-levels >= 100 µg/plate in the three strains without S9 mix, and at dose-levels >= 500 µg/plate in the three strains with S9 mix. Since the test item was found to be toxic in the preliminary test, the selection of the highest dose-level to be used in the mutagenicity experiments was based on the level of toxicity, according to the criteria specified in the international guidelines.The mean number of revertants for the vehicle and positive controls met the acceptance criteria. Also, there were six analysable dose-levels for each strain and test condition. The study was therefore considered to be valid. No precipitate was observed in the Petri plates when scoring the revertants, at any of the tested dose-levels.
The selected dose-levels were 0.69, 2.06, 6.17, 18.5, 55.6 and 166.7 µg/plate without S9 for the five strains in both mutagenicity experiments. A moderate to strong toxicity (thinning of the bacterial lawn and/or decrease in the number of revertants) was noted at 166.7 µg/plate towards the five strains in the first experiment, then at dose-levels >= 55.6 µg/plate in the TA 102 strain and >=18.5 µg/plate in the TA 1535, TA 1537, TA 98 and TA 100 strains in the second experiment. The selected dose-levels were 2.06, 6.17, 18.5, 55.6, 166.7 and 500 µg/plate with S9 for the five strains in both mutagenicity experiments. A strong toxicity (thinning of the bacterial lawn and/or decrease in the number of revertants) was noted at the highest tested dose-level of 500 µg/plate towards the five strains used in both mutagenicity experiments. The test item did not induce any noteworthy increase in the number of revertants, in either experiment, in any of the five tested strains.
LUPEROX 221 did not show any mutagenic activity in the bacterial reverse mutation test withSalmonella typhimuriumstrains, either in the presence or absence of a rat liver metabolizing system.
Link to relevant study records
- Endpoint:
- in vitro gene mutation study in bacteria
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Study period:
- 02 March 2016 - 08 April 2016
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- guideline study
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 471 (Bacterial Reverse Mutation Assay)
- Qualifier:
- according to guideline
- Guideline:
- EU Method B.13/14 (Mutagenicity - Reverse Mutation Test Using Bacteria)
- GLP compliance:
- yes (incl. QA statement)
- Type of assay:
- bacterial reverse mutation assay
- Target gene:
- Histidine operon
- Species / strain / cell type:
- S. typhimurium TA 1535, TA 1537, TA 98, TA 100 and TA 102
- Metabolic activation:
- with and without
- Metabolic activation system:
- rat liver S9 mix
- Test concentrations with justification for top dose:
- The selected dose-levels for the main mutagenicity experiments were the following (based on the toxicity observed in the preliminary test):without S9 mix: 0.69, 2.06, 6.17, 18.5, 55.6 and 166.7 µg/plate for the five strains in both mutagenicity experiments. with S9 mix: 2.06, 6.17, 18.5, 55.6, 166.7 and 500 µg/plate for the five strains in both mutagenicity experiments.
- Vehicle / solvent:
- - Vehicle: ethanol - Justification for choice of vehicle: test item was found to be freely soluble in the vehicle at the concentration of 200 mg/mL.
- Untreated negative controls:
- no
- Negative solvent / vehicle controls:
- yes
- True negative controls:
- no
- Positive controls:
- yes
- Positive control substance:
- 9-aminoacridine
- 2-nitrofluorene
- sodium azide
- benzo(a)pyrene
- mitomycin C
- other: 2-Anthramine
- Details on test system and experimental conditions:
- METHOD OF APPLICATION: in agar.DURATION- Preincubation period: 60 minutes- Incubation time: 48 to 72 hours.DETERMINATION OF TOXICITY- Method: decrease in number of revertant colonies and/or a thinning of the bacterial lawn.
- Evaluation criteria:
- In all cases, biological relevance (such as reproducibility and reference to historical data) was taken into consideration when evaluating the results.The test item is considered to have shown mutagenic activity in this study if:- a reproducible 2-fold increase (for the TA 98, TA 100 and TA 102 strains) or 3-fold increase (for the TA 1535 and TA 1537 strains) in the mean number of revertants compared with the vehicle controls is observed, in any strain, at any dose-level,- and/or a reproducible dose-response relationship is evidenced.The test item is considered to have shown no mutagenic activity in this study if:- neither an increase in the mean number of revertants, reaching 2-fold (for the TA 98, TA 100 and TA 102 strains) or 3-fold (for the TA 1535 and TA 1537 strains) the vehicle controls value, is observed at any of the tested dose-levels, - nor any evidence of a dose-response relationship is noted.
- Key result
- Species / strain:
- S. typhimurium, other: TA 1535, TA 1537, TA 98, TA 100 and TA 102
- Metabolic activation:
- with
- Genotoxicity:
- negative
- Cytotoxicity / choice of top concentrations:
- cytotoxicity
- Vehicle controls validity:
- valid
- Untreated negative controls validity:
- not applicable
- Positive controls validity:
- valid
- Additional information on results:
- The mean number of revertants for the vehicle and positive controls met the acceptance criteria. Also, there were at least five analysable dose-levels for each strain and test condition. The study was therefore considered to be valid.
Since the test item was found to be toxic in the preliminary test, the selection of the highest dose-level to be used in the mutagenicity experiments was based on the level of toxicity, according to the criteria specified in the international guidelines.
Experiments without S9 mix
The selected dose-levels were 0.69, 2.06, 6.17, 18.5, 55.6 and 166.7 µg/plate for the five strains in both mutagenicity experiments.
No precipitate was observed in the Petri plates when scoring the revertants, at any of the tested dose levels.
A moderate to strong toxicity (thinning of the bacterial lawn and/or decrease in the number of revertants) was noted at 166.7 µg/plate towards the five strains in the first experiment, then at dose-levels = 55.6 µg/plate in the TA 102 strain and = 18.5 µg/plate in the TA 1535, TA 1537, TA 98 and TA 100 strains in the second experiment.
The test item did not induce any noteworthy increase in the number of revertants, in either experiment, in any of the five tested strains.
Experiments with S9 mix
The selected dose-levels were 2.06, 6.17, 18.5, 55.6, 166.7 and 500 µg/plate for the five strains in both mutagenicity experiments.
No precipitate was observed in the Petri plates when scoring the revertants, at any of the tested dose levels.
A strong toxicity (thinning of the bacterial lawn and/or decrease in the number of revertants) was noted at the highest tested dose-level of 500 µg/plate towards the five strains used in both mutagenicity experiments.
The test item did not induce any noteworthy increase in the number of revertants, in either experiment, in any of the five tested strains. - Conclusions:
- LUPEROX 221 did not show any mutagenic activity in the bacterial reverse mutation test with Salmonella typhimurium strains, either in the presence or absence of a rat liver metabolizing system.
- Executive summary:
The potential of LUPEROX 221 to induce reverse mutations was evaluated in Salmonella typhimurium. The study was performed according to the international guidelines and in compliance with the principles of Good Laboratory Practice. A preliminary toxicity test was performed to define the dose-levels of LUPEROX 221, dissolved in ethanol, to be used for the mutagenicity experiments. The test item was then tested in two independent experiments, both with and without a metabolic activation system, the S9 mix, prepared from a liver post-mitochondrial fraction (S9 fraction) of rats induced with Aroclor 1254. Treatments were performed according to the direct plate incorporation method except for the second experiment with S9 mix, which was performed according to the pre-incubation method (60 minutes, 37°C). Five strains of bacteria Salmonella typhimurium were used: TA 1535, TA 1537, TA 98, TA 100 and TA 102. Each strain was exposed to six dose-levels of the test item (three plates/dose-level). After 48 to 72 hours of incubation at, the revertant colonies were scored. The evaluation of the toxicity was performed on the basis of the observation of the decrease in the number of revertant colonies and/or a thinning of the bacterial lawn.
According to available solubility data, the test item was found to be freely soluble in the vehicle at the concentration of 200 mg/mL. Consequently, using a maximum treatment-volume of 25 µL/plate, the dose-levels used for the preliminary toxicity test were 10, 100, 500, 1000, 2500 and 5000 µg/plate. No precipitate was observed in the Petri plates when scoring the revertants, at any of the tested dose-levels. A strong toxicity (thinning of the bacterial lawn and/or decrease in the number of revertants) was noted at dose-levels >= 100 µg/plate in the three strains without S9 mix, and at dose-levels >= 500 µg/plate in the three strains with S9 mix. Since the test item was found to be toxic in the preliminary test, the selection of the highest dose-level to be used in the mutagenicity experiments was based on the level of toxicity, according to the criteria specified in the international guidelines. The mean number of revertants for the vehicle and positive controls met the acceptance criteria. Also, there were six analysable dose-levels for each strain and test condition. The study was therefore considered to be valid. No precipitate was observed in the Petri plates when scoring the revertants, at any of the tested dose-levels.
The selected dose-levels were 0.69, 2.06, 6.17, 18.5, 55.6 and 166.7 µg/plate without S9 for the five strains in both mutagenicity experiments. A moderate to strong toxicity (thinning of the bacterial lawn and/or decrease in the number of revertants) was noted at 166.7 µg/plate towards the five strains in the first experiment, then at dose-levels >= 55.6 µg/plate in the TA 102 strain and >=18.5 µg/plate in the TA 1535, TA 1537, TA 98 and TA 100 strains in the second experiment. The selected dose-levels were 2.06, 6.17, 18.5, 55.6, 166.7 and 500 µg/plate with S9 for the five strains in both mutagenicity experiments. A strong toxicity (thinning of the bacterial lawn and/or decrease in the number of revertants) was noted at the highest tested dose-level of 500 µg/plate towards the five strains used in both mutagenicity experiments. The test item did not induce any noteworthy increase in the number of revertants, in either experiment, in any of the five tested strains.
LUPEROX 221 did not show any mutagenic activity in the bacterial reverse mutation test with Salmonella typhimurium strains, either in the presence or absence of a rat liver metabolizing system.
Reference
Endpoint conclusion
- Endpoint conclusion:
- no adverse effect observed (negative)
Additional information
Justification for classification or non-classification
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