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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
![](https://echa.europa.eu/o/diss-blank-theme/images/factsheets/A-REACH/factsheet/print_toxicological-information.png)
Genetic toxicity: in vivo
Administrative data
- Endpoint:
- in vivo mammalian somatic cell study: cytogenicity / erythrocyte micronucleus
- Remarks:
- Type of genotoxicity: other: clastogenicity/aneugenicity
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Study period:
- 2012-04-13 to 2012-06-15
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- other: GLP guideline study
Data source
Reference
- Reference Type:
- study report
- Title:
- Unnamed
- Year:
- 2 012
- Report date:
- 2012
Materials and methods
Test guidelineopen allclose all
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 474 (Mammalian Erythrocyte Micronucleus Test)
- Deviations:
- no
- Qualifier:
- according to guideline
- Guideline:
- EU Method B.12 (Mutagenicity - In Vivo Mammalian Erythrocyte Micronucleus Test)
- Deviations:
- no
- Qualifier:
- according to guideline
- Guideline:
- EPA OPPTS 870.5395 (In Vivo Mammalian Cytogenetics Tests: Erythrocyte Micronucleus Assay)
- Deviations:
- no
- GLP compliance:
- yes (incl. QA statement)
- Remarks:
- Bayerisches Landesamt für Gesundheit und Lebensmittelsicherheit, München, Germany
- Type of assay:
- micronucleus assay
Test material
Constituent 1
Test animals
- Species:
- mouse
- Strain:
- NMRI
- Sex:
- male/female
- Details on test animals or test system and environmental conditions:
- TEST ANIMALS
- Source: Charles River, 97633 Sulzfeld, Germany
- Age at study initiation: minimum 7 weeks
- Assigned to test groups randomly: yes
- Fasting period before study:
- Housing: 5 animals of identical sex per cage, IVC cage (Polysulphone), Type II L
- Diet (ad libitum): Altromin 1324 maintenance diet for rats and mice
- Water (ad libitum): tap water, sulphur acidified to pH value of approx. 2.8 (drinking water, municipal residue control, micro-biologically controlled at frequent intervals)
- Acclimation period: 5 days
ENVIRONMENTAL CONDITIONS
- Temperature (°C): 22 ± 3 °C
- Humidity (%): 55 ± 10%
- Air changes (per hr): at least 10 x per hour
- Photoperiod (hrs dark / hrs light): artificial light 6:00 - 18:00
IN-LIFE DATES: From: To:
Administration / exposure
- Route of administration:
- intraperitoneal
- Vehicle:
- - Vehicle(s)/solvent(s) used: physiol. saline
- Justification for choice of solvent/vehicle: The solvent was chosen based on best solubility of the test item and according to its relative non-toxicity for the animals.
- Concentration of test material in vehicle: 10 mg/mL (1 MTD), 5 mg/mL (0.5 MTD), 2 mg/mL (0.2 MTD)
- Amount of vehicle (if gavage or dermal): 10 mL per kg body weight
- Lot/batch no. (if required): 111036, 111214 AlleMan Pharma - Details on exposure:
- PREPARATION OF DOSING SOLUTIONS:
The test item was prepared and diluted in 0.9% NaCl within 1 h before treatment. All animals received a single volume ip of 10 mL/kg bw. - Frequency of treatment:
- The animals received the test item once ip.
- Post exposure period:
- Sampling of the peripheral blood was carried out on animals 44 h (all control and dose groups) and 68 h (negative control, 1 MTD group) after treatment.
Doses / concentrations
- Remarks:
- Doses / Concentrations:
three dose groups: 1 MTD (100 mg/kg bw), 0.5 MTD (50 mg/kg bw), 0.2 MTD (20 mg/kg bw)
Basis:
other: dilution in 0.9% NaCl
- No. of animals per sex per dose:
- 5
- Control animals:
- yes, concurrent vehicle
- Positive control(s):
- cyclophosphamide
- Justification for choice of positive control: clastogenic control substance, good stability at room temperature, broad basis of historical laboratory control data
- Route of administration: intraperitoneal
- Doses / concentrations: 40 mg/kg body weight
Examinations
- Tissues and cell types examined:
- peripheral blood erythrocytes
- Details of tissue and slide preparation:
- CRITERIA FOR DOSE SELECTION:
A preceding study on toxicity was performed with the same strain and under identical conditions as in the main study. Five male animals and three female animals were treated ip for detection of the maximum tolerable dose. The maximum dose that was applied was 2000 mg/kg bw according the OECD 474 guideline. The maximum volume which was administered was 10 mL/kg bw.
The highest dose group evaluated in the main experiment (100 mg/kg bw) based on the toxicity observed in the pre-experiment.
METHOD OF ANALYSIS:
Evaluation of all samples, including those of positive and negative controls, was performed using a flow cytometer (FACScan, BD Biosciences). Anti-CD71 antibodies were labelled with Fluorescein-isothiocyanate (FITC), anti-CD61 antibodies were labelled with Phycoerythrin (PE). Particles were differentiated using Forward Scatter (FSC) and Side Scatter (SSC) parameters of the flow cytometer. Fluorescence intensity were recorded on the FL1, FL2 and FL3 channels for FITC, PE and PI respectively. At least 10000 immature erythrocytes per animal were scored for the incidence of micronucleated immature erythrocytes. To detect an eventually occurring cytotoxic effect of the test item the ratio between immature and mature erythrocytes was determined. The results were expressed as relative PCE (rel. PCE = proportion of polychromatic (immature) erythrocytes among total erythrocytes). - Evaluation criteria:
- There are several criteria for determining a positive result:
- dose-related increase in the number of micronucleated cells and/or
- biologically relevant increase in the number of micronucleated cells for at least one of the dose groups.
According to the OECD guideline, the biological relevance as well as the statistical significance of the results are the criterion for the interpretation.
A test item is considered to be negative if there is no biologically relevant and/or statistically significant increase in the number of micronucleated cells at any dose level. - Statistics:
- For the statistics the nonparametric Mann-Whitney Test was used. However, both biological relevance and statistical significance were considered together.
Results and discussion
Test results
- Sex:
- male/female
- Genotoxicity:
- negative
- Toxicity:
- yes
- Vehicle controls validity:
- valid
- Positive controls validity:
- valid
- Additional information on results:
- RESULTS OF RANGE-FINDING STUDY
- Clinical signs of toxicity in test animals:
In the pre-experiment a concentration of 200 mg/mL of the test item was evaluated. One male mouse received a single dose of 2000 mg/kg bw ip and showed toxicity such as reduction of spontaneous activity, kyphosis, muscle twitches, opisthotonos and half eyelid closure. The animal died 24 minutes after the treatment.
One male mouse received a single dose of 500 mg/kg bw ip and showed strong toxicity, such as reduction of spontaneous activity, recumbency, kyphosis, bradykinesia, opisthotonos, muscle twitches, ataxia, piloerection, and half eyelid closure. The animal died 2 hours after the treatment.
Three male and three female mice received a single dose of 100 mg/kg bw ip and showed toxicity, such as reduction of spontaneous activity, constricted abdomen, piloerection, recumbency, opisthotonos, ataxia, muscle twitches, kyphosis and half eyelid closure. Additionally, the skin and urine of the animals were blue coloured by the test item.
RESULTS OF DEFINITIVE STUDY
- Induction of micronuclei (for Micronucleus assay):
The negative controls (44 h and 68 h) evaluated were within the range of the historical control data of the negative control (0.08 – 0.43%). The mean values of micronuclei observed for the negative control (44 h) were 0.21% for male and 0.28% for female mice. The mean values for the 68 h negative control were 0.32% for the male and 0.12% for the female mice.
The mean values of micronuclei observed after treatment with 0.2 MTD were 0.31% for male and 0.11% for female mice. The value observed in male group was slightly increased compared to the corresponding negative control. The value observed in female group was slightly reduced as compared to the corresponding negative control, but this increase/decrease was not statistically significant. Additionally, both values were within the range of the historical negative control data.
The mean values noted for the 0.5 MTD dose group were 0.12% for male and 0.26% for female mice. The values observed in the male and female group were decreased as compared to the corresponding negative control. However, both values were within the range of the historical negative control data.
The dose group treated with 1 MTD (44 h treatment) showed mean values of 0.14% for male and 0.38% for female mice. The value observed in male group was reduced compared to the corresponding negative control. The value observed in female group was increased compared to the corresponding negative control, however this increase was not statistically significant. Additionally, both values were within the range of the historical negative control data.
The mean values observed for the 1 MTD 68 h treatment were 0.25% for the male and 0.33% for the female mice. These values were within the range of the corresponding negative control.
No biologically relevant increase of micronuclei was found after treatment with the test item in any of the dose groups evaluated.
- Ratio of PCE/NCE (for Micronucleus assay):
The negative controls (44 h, 68 h) were within the range of the historical control data of the negative control (1.19-3.97). The mean values noted for the 44 h negative control were 3.05 for the male and 1.45 for the female mice. The mean values detected for the 68 h negative control were 3.14 for the male and 1.62 for the female mice.
The animal group treated with 0.2 MTD showed mean values of the relative PCE of 2.93 (male mice) and 1.45 (female mice). The mean values observed in the male and in the female group were within the range of the corresponding control and within the range of the historical control data.
The dose groups which were treated with 0.5 MTD showed mean values of the relative PCE of 2.59 (male mice) and 1.40 (female mice). The values observed in the male and female group were decreased compared to the corresponding negative control. However, both values were within the range of the historical control data.
The animals who received 1 MTD (44 h treatment) showed mean values of 2.77 (male mice) and 1.24 (female mice). The values observed in the male and female group were decreased compared to the corresponding negative control.
The animal group which was treated with 1 MTD (68 h treatment) showed mean values of the relative PCE of 2.07 (male mice) and 0.89 (female mice). The values observed in the male and female group were decreased compared to the corresponding negative control.
- Statistical evaluation:
The nonparametric Mann-Whitney Test was performed to verify the results. No statistically significant increases (p<0.05) of cells with micronuclei were noted in the dose groups of the test item evaluated.
Applicant's summary and conclusion
- Conclusions:
- Interpretation of results (migrated information): negative
In conclusion, it can be stated that during the study described and under the experimental conditions reported, the test item FAT 40853/A TE did not induce structural and/or numerical chromosomal damage in the immature erythrocytes of the mouse.
Therefore, the test item FAT 40853/A TE is considered to be non-mutagenic with respect to clastogenicity and/or aneugenicity in the Mammalian Erythrocyte Micronucleus Test. - Executive summary:
In a NMRI mouse peripheral blood micronucleus assay, five male and female animals per dose group were treated ip with FAT 40853/A TE at doses of 20, 50 and 100 mg/kg bw. Peripheral blood cells were harvested at 44 h (all dose and control groups) and 68 h (negative control and 1 MTD group) post-treatment. The vehicle was 0.9% NaCl. The animals received the test item once ip.
There were signs of toxicity during the study. The animals treated with doses of 0.2 and 0.5 MTD showed slight and moderate signs of systemic toxicity, respectively. The animals treated with a dose of 1 MTD showed signs of systemic toxicity such as reduction of spontaneous activity, constricted abdomen, piloerection, bradykinesia, catalepsis, recumbency, opisthotonos, half eyelid closure and eye closure.FAT 40853/ A TE was tested at an adequate dose based on OECD 474. The positive control induced the appropriate response. There was no significant increase in the frequency of micronucleated polychromatic erythrocytes in peripheral blood cells after any treatment time.
This study is classified asacceptable. This study satisfies the requirement for Test Guideline OPPTS 870.5395; OECD 474 for in vivo cytogenetic mutagenicity data.
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.
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