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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
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:
- 2 016
- Report date:
- 2016
Materials and methods
Test guideline
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 471 (Bacterial Reverse Mutation Assay)
- GLP compliance:
- yes (incl. QA statement)
- Type of assay:
- bacterial reverse mutation assay
Test material
- Reference substance name:
- Reaction products of 3-Methylaniline with heptyl naphthalen-2-ol
- Cas Number:
- 1619917-05-3
- Molecular formula:
- Not applicable (UVCB Substance)
- IUPAC Name:
- Reaction products of 3-Methylaniline with heptyl naphthalen-2-ol
- Test material form:
- solid
Constituent 1
- Specific details on test material used for the study:
- SOURCE OF TEST MATERIAL
- batch No.of test material: 78-231-15
- Expiration date of the batch: October 2017
STABILITY AND STORAGE CONDITIONS OF TEST MATERIAL
- Storage condition of test material: room temperature, protected from light
Method
- Target gene:
- histidine
Species / strain
- 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
- Test concentrations with justification for top dose:
- 3.16, 10.0, 31.6, 100, 316, 1000, 2500 and 5000 μg/plate
- Vehicle / solvent:
- acetone
Controls
- Untreated negative controls:
- yes
- Negative solvent / vehicle controls:
- yes
- Positive controls:
- yes
- Positive control substance:
- sodium azide
- methylmethanesulfonate
- other: 4-nitro-o-phenylene-diamine; 2-aminoanthracene; Congo Red
- Details on test system and experimental conditions:
- METHOD OF APPLICATION
The test item was suspended in acetone and diluted prior to treatment. For the plate incorporation
method in experiment I a stock solution of 50 mg/mL was used for preparation of the dilution series.
For the pre-incubation method in experiment II a stock solution of 100 mg/mL was used. So a lower
amount could be applied by performing the pre-incubation and so the solvent was compatible with
the survival of the bacteria and the S9 activity.
Preparation of Bacteria
Samples of each tester strain were grown by culturing for 12 h at 37 °C in Nutrient Broth to the late
exponential or early stationary phase of growth (approx. 109 cells/mL). The nutrient medium consists
per litre:
8 g Nutrient Broth
5 g NaCl
A solution of 125 μL ampicillin (10 mg/mL) (TA 98, TA 100, TA 102) was added in order to retain the
phenotypic characteristics of the strain.
Pre-Experiment for Toxicity
The toxicity of the test item was determined with tester strains TA 98 and TA 100 in a preexperiment.
Eight concentrations were tested for toxicity and induction of mutations with three plates
each. The experimental conditions in this pre-experiment were the same as described below for the
main experiment I (plate incorporation test).
Toxicity may be detected by a clearing or rather diminution of the background lawn or a reduction in
the number of revertants down to a mutation factor of approximately ≤ 0.5 in relation to the solvent
control.
The test item was tested in the pre-experiment with the following concentrations:
3.16, 10.0, 31.6, 100, 316, 1000, 2500 and 5000 μg/plate
Exposure Concentrations
The test item concentrations to be applied in the main experiments were chosen according to the
results of the pre-experiment (see chapter 12.1.1 Pre-Experiment). 5000 μg/plate was selected as
the maximum concentration. The concentration range covered two logarithmic decades.
Two independent experiments were performed with the following concentrations:
3.16, 10.0, 31.6, 100, 316, 1000, 2500 and 5000 μg/plate
As the results of the pre-experiment were in accordance with the criteria described above, these
were reported as a part of the main experiment I.
Experimental Performance
For the plate incorporation method with rat liver S9 the following materials were mixed in a test tube
and poured over the surface of a minimal agar plate:
100 μL Test solution at each dose level, solvent control, negative control or reference
mutagen solution (positive control),
500 μL S9 mix (for testing with metabolic activation) or S9 mix substitution buffer (for
testing without metabolic activation),
100 μL Bacteria suspension (cf. Preparation of Bacteria, pre-culture of the strain),
2000 μL Overlay agar.
For the pre-incubation method with hamster liver S9 the following materials were mixed in a test tube
and incubated for 30 min. at 30 °C :
50 μL Test extract at each dose level, extract medium control, or
100 μL Negative control or reference mutagen solution (positive control),
500 μL S9 mix (for testing with metabolic activation) or S9 mix substitution buffer (for
testing without metabolic activation),
100 μL Bacteria suspension (cf. Preparation of Bacteria, pre-culture of the strain),
After the incubation period (30 min., 30 °C), the overlay agar (2000 μL) was added and poured onto
the surface of a minimal agar plate.
For each strain and dose level, including the controls, three plates (in a few cases only two plates
were evaluated, see Table 2: Results Experiment I) were used.
After solidification the plates were inverted and incubated at 37 °C for at least 48 h in the dark.
Data Recording
The colonies were counted using a ProtoCOL counter (Meintrup DWS Laborgeräte GmbH). If
precipitation of the test item precluded automatic counting the revertant colonies were counted by
hand. In addition, tester strains with a low spontaneous mutation frequency like TA 1535 and
TA 1537 were counted manually.
Evaluation of Cytotoxicity
Cytotoxicity can be detected by a clearing or rather diminution of the background lawn (indicated as
"N" or "B", respectively in the result tables) or a reduction in the number of revertants down to a
mutation factor of approximately ≤ 0.5 in relation to the solvent control. - Evaluation criteria:
- The Mutation Factor is calculated by dividing the mean value of the revertant counts by the mean
values of the solvent control (the exact and not the rounded values are used for calculation).
A test item is considered as mutagenic if:
- a clear and dose-related increase in the number of revertants occurs and/or
- a biologically relevant positive response for at least one of the dose groups occurs in at least one tester strain with or without metabolic activation.
A biologically relevant increase is described as follows:
- if in tester strains TA 98, TA 100 and TA 102 the number of reversions is at least twice as high
- if in tester strains TA 1535 and TA 1537 the number of reversions is at least three times higher than the reversion rate of the solvent control.
According to OECD guidelines, the biological relevance of the results is the criterion for the
interpretation of results, a statistical evaluation of the results is not regarded as necessary.
A test item producing neither a dose related increase in the number of revertants nor a reproducible
biologically relevant positive response at any of the dose groups is considered to be non-mutagenic
in this system.
Results and discussion
Test resultsopen allclose all
- Species / strain:
- S. typhimurium TA 98
- Remarks:
- in Exp I
- Metabolic activation:
- without
- Genotoxicity:
- negative
- Cytotoxicity / choice of top concentrations:
- cytotoxicity
- Remarks:
- at 1000 μg/plate and higer
- Species / strain:
- S. typhimurium TA 100
- Remarks:
- in Exp I
- Metabolic activation:
- with and without
- Genotoxicity:
- negative
- Cytotoxicity / choice of top concentrations:
- cytotoxicity
- Remarks:
- at concentrations of 316 μg/plate and higher (without metabolic activation) and at a concentration of 5000 μg/plate (with metabolic activation).
- Species / strain:
- S. typhimurium TA 1537
- Remarks:
- in Exp I
- Metabolic activation:
- without
- Genotoxicity:
- negative
- Cytotoxicity / choice of top concentrations:
- cytotoxicity
- Remarks:
- at concentrations of 2500 μg/plate and higher
- Species / strain:
- S. typhimurium TA 98
- Remarks:
- in Exp II
- Metabolic activation:
- without
- Genotoxicity:
- negative
- Cytotoxicity / choice of top concentrations:
- cytotoxicity
- Remarks:
- at concentrations of 2500 μg/plate and higher
- Species / strain:
- other: TA 100, TA1535 and TA1537
- Metabolic activation:
- without
- Genotoxicity:
- negative
- Cytotoxicity / choice of top concentrations:
- cytotoxicity
- Remarks:
- at concentrations of 316 μg/plate and higher
Any other information on results incl. tables
Precipitation of the test item was observed in all tester strains used in experiment I at concentrations of 2500 μg/plate and higher (with metabolic activation).
Toxic effects of the test item were noted in several tester strains evaluated in experiment I and II.
In experiment I toxic effects of the test item were observed in tester strain TA 98 at concentrations of
1000 μg/plate and higher (without metabolic activation). In tester strain TA 100 toxic effects of the
test item were noted at concentrations of 316 μg/plate and higher (without metabolic activation) and
at a concentration of 5000 μg/plate (with metabolic activation). In tester strain TA 1537 toxic effects
of the test item were observed at concentrations of 2500 μg/plate and higher (without metabolic
activation).
In experiment II toxic effects of the test item were noted in tester strain TA 98 at concentrations of
2500 μg/plate and higher (without metabolic activation). In tester strains TA 100, TA 1535 and
TA 1537 toxic effects of the test item were noted at concentrations of 316 μg/plate and higher
(without metabolic activation).
The reduction in the number of revertants down to a mutation factor of ≤ 0.5 found in experiment I in
tester strain TA 1535 at a concentration of 3.16 μg/plate (with metabolic activation), in experiment II
in tester strain TA 100 at a concentration of 316 μg/plate (with metabolic activation) and in tester
strain TA 1537 at a concentration of 2500 μg/plate (with metabolic activation) was regarded as not
biologically relevant due to lack of a dose-response relationship. The reduction in the number of
revertants down to a mutation factor of ≤ 0.5 found in experiment I in the negative control of tester
strain TA 1537 (with metabolic activation) was regarded as not biologically relevant due to the fact
that all three numbers of spontaneous revertants were within the historical control data and lack of
concomitant clearing of the background lawn.
No biologically relevant increases in revertant colony numbers of any of the five tester strains were
observed following treatment with RED 2596 at any concentration level, neither in the presence nor
absence of metabolic activation in experiment I and II.
All criteria of validity were met
Applicant's summary and conclusion
- Conclusions:
- It can be stated that during the described mutagenicity test and under the experimental conditions reported, RED 2596 did not cause gene mutations by base pair changes or frameshifts in the genome of the tester strains used.
Therefore, RED 2596 is considered to be non-mutagenic in this bacterial reverse mutation assay. - Executive summary:
The test item RED 2596 was investigated for its potential to induce gene mutations according to the
plate incorporation test with rat liver S9 (experiment I) and the pre-incubation test with hamster liver
S9 (experiment II) using Salmonella typhimurium strains TA 98, TA 100, TA 1535, TA 1537 and
TA 102.
In two independent experiments several concentrations of the test item were used. Each assay was
conducted with and without metabolic activation. The concentrations, including the controls, were
tested in triplicate. The following concentrations of the test item were prepared and used in the
experiments:
3.16, 10.0, 31.6, 100, 316, 1000, 2500 and 5000 μg/plate
Precipitation of the test item was observed in all tester strains used in experiment I at concentrations
of 2500 μg/plate and higher (with metabolic activation).
Toxic effects of the test item were noted in several tester strains evaluated in experiment I and II.
In experiment I toxic effects of the test item were observed in tester strain TA 98 at concentrations of
1000 μg/plate and higher (without metabolic activation). In tester strain TA 100 toxic effects of the
test item were noted at concentrations of 316 μg/plate and higher (without metabolic activation) and
at a concentration of 5000 μg/plate (with metabolic activation). In tester strain TA 1537 toxic effects
of the test item were observed at concentrations of 2500 μg/plate and higher (without metabolic
activation).
In experiment II toxic effects of the test item were noted in tester strain TA 98 at concentrations of
2500 μg/plate and higher (without metabolic activation). In tester strains TA 100, TA 1535 and
TA 1537 toxic effects of the test item were noted at concentrations of 316 μg/plate and higher
(without metabolic activation).
The reduction in the number of revertants down to a mutation factor of ≤ 0.5 found in experiment I in
tester strain TA 1535 at a concentration of 3.16 μg/plate (with metabolic activation), in experiment II
in tester strain TA 100 at a concentration of 316 μg/plate (with metabolic activation) and in tester
strain TA 1537 at a concentration of 2500 μg/plate (with metabolic activation) was regarded as not
biologically relevant due to lack of a dose-response relationship. The reduction in the number of
revertants down to a mutation factor of ≤ 0.5 found in experiment I in the negative control of tester
strain TA 1537 (with metabolic activation) was regarded as not biologically relevant due to the fact
that all three numbers of spontaneous revertants were within the historical control data and lack of
concomitant clearing of the background lawn.
No biologically relevant increases in revertant colony numbers of any of the five tester strains were
observed following treatment with RED 2596 at any concentration level, neither in the presence nor
absence of metabolic activation in experiment I and II.
In conclusion, it can be stated that during the described mutagenicity test and under the
experimental conditions reported, RED 2596 did not cause gene mutations by base pair changes or
frameshifts in the genome of the tester strains used.
Therefore, RED 2596 is considered to be non-mutagenic in this bacterial reverse mutation assay.
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