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EC number: 203-312-7 | CAS number: 105-59-9
- 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
Endpoint summary
Administrative data
Key value for chemical safety assessment
Genetic toxicity in vitro
Description of key information
MDEA was evaluated for potential genotoxic activity using the Salmonella/microsome reverse gene mutation test (similar to OECD 471, no GLP), the CHO/HGPRT forward gene mutation test (similar to OECD 476, no GLP), and a sister chromatid exchange test in cultured CHO cells (similar to OECD 479, no GLP). MDEA did not produce any significant or dose-related increases in the frequencies of gene mutations, chromosome aberrations, sister chromatid exchanges or micronuclei. These results indicate that MDEA is not genotoxic in the tests conducted.
Link to relevant study records
- Endpoint:
- in vitro gene mutation study in bacteria
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- study well documented, meets generally accepted scientific principles, acceptable for assessment
- Qualifier:
- equivalent or similar to guideline
- Guideline:
- OECD Guideline 471 (Bacterial Reverse Mutation Assay)
- Principles of method if other than guideline:
- Method according to Ames et al (1975)
- GLP compliance:
- not specified
- Type of assay:
- bacterial reverse mutation assay
- Target gene:
- histidine gene
- Species / strain / cell type:
- other: Salmonella typhimurium TA98, TA100, TA1535, TA1537, TA1538
- Metabolic activation:
- with and without
- Metabolic activation system:
- Type and composition of metabolic activation system:
- source of S9 : S9 liver homogenate, isolated from Aroclor 1254 induced rat - Test concentrations with justification for top dose:
- 0.1, 0.3, 1, 3, 5, 10 mg/plate
- Vehicle / solvent:
- water
- Untreated negative controls:
- yes
- Negative solvent / vehicle controls:
- yes
- True negative controls:
- no
- Positive controls:
- yes
- Positive control substance:
- sodium azide
- Remarks:
- without S9 mix
- Untreated negative controls:
- yes
- Negative solvent / vehicle controls:
- yes
- True negative controls:
- no
- Positive controls:
- yes
- Positive control substance:
- 9-aminoacridine
- Remarks:
- without S9 mix
- Untreated negative controls:
- yes
- Negative solvent / vehicle controls:
- yes
- True negative controls:
- no
- Positive controls:
- yes
- Positive control substance:
- other: 4-nitrophenylenediamin
- Remarks:
- without S9 mix
- Untreated negative controls:
- yes
- Negative solvent / vehicle controls:
- yes
- True negative controls:
- no
- Positive controls:
- yes
- Positive control substance:
- other: 2-aminoanthracen
- Remarks:
- with S9 mix
- Details on test system and experimental conditions:
- METHOD OF APPLICATION: in agar (plate incorporation)
DURATION
- Exposure duration: 48-72 h
NUMBER OF REPLICATIONS: 3
DETERMINATION OF CYTOTOXICITY
- Method: inhibition of growth of the background lawn
- Evaluation criteria:
- At least twice the solvent control for at least one concentration and there was evidence of a concentration-related increase in the number of revertant colonies.
- Statistics:
- no data
- Key result
- Species / strain:
- S. typhimurium TA 98
- Metabolic activation:
- with and without
- Genotoxicity:
- negative
- Cytotoxicity / choice of top concentrations:
- cytotoxicity
- Remarks:
- -S9 mix: from 3 mg/plate onwards; +S9-mix: at 10 mg/plate
- Vehicle controls validity:
- valid
- Untreated negative controls validity:
- valid
- Positive controls validity:
- valid
- Key result
- Species / strain:
- S. typhimurium TA 100
- Metabolic activation:
- with and without
- Genotoxicity:
- negative
- Cytotoxicity / choice of top concentrations:
- cytotoxicity
- Remarks:
- -S9 mix: from 3 mg/plate onwards; +S9-mix: at 10 mg/plate
- Vehicle controls validity:
- valid
- Untreated negative controls validity:
- valid
- Positive controls validity:
- valid
- Key result
- Species / strain:
- S. typhimurium TA 1535
- Metabolic activation:
- with and without
- Genotoxicity:
- negative
- Cytotoxicity / choice of top concentrations:
- cytotoxicity
- Remarks:
- -S9 mix: from 3 mg/plate onwards; +S9-mix: at 10 mg/plate
- Vehicle controls validity:
- valid
- Untreated negative controls validity:
- valid
- Positive controls validity:
- valid
- Key result
- Species / strain:
- S. typhimurium TA 1537
- Metabolic activation:
- with and without
- Genotoxicity:
- negative
- Cytotoxicity / choice of top concentrations:
- cytotoxicity
- Remarks:
- -S9 mix: from 3 mg/plate onwards; +S9-mix: at 10 mg/plate
- Vehicle controls validity:
- valid
- Untreated negative controls validity:
- valid
- Positive controls validity:
- valid
- Key result
- Species / strain:
- S. typhimurium TA 1538
- Metabolic activation:
- with and without
- Genotoxicity:
- negative
- Cytotoxicity / choice of top concentrations:
- cytotoxicity
- Remarks:
- -S9 mix: from 3 mg/plate onwards; +S9-mix: at 10 mg/plate
- Vehicle controls validity:
- valid
- Untreated negative controls validity:
- valid
- Positive controls validity:
- valid
- Additional information on results:
- No mutagenic activity was observed in any of the 5 strains mutants over the range of concentrations tested in the absence or the presence of S9 activation, either by evidence of a dose-response relation or a doubling of the mean number of colonies over the vehicle control value.
- Endpoint:
- in vitro gene mutation study in mammalian cells
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- study well documented, meets generally accepted scientific principles, acceptable for assessment
- Qualifier:
- equivalent or similar to guideline
- Guideline:
- OECD Guideline 476 (In Vitro Mammalian Cell Gene Mutation Test)
- Principles of method if other than guideline:
- CHO/HGPRT forward gene mutation test according to O'Neill (1977)
- GLP compliance:
- not specified
- Type of assay:
- in vitro mammalian cell transformation assay
- Species / strain / cell type:
- Chinese hamster Ovary (CHO)
- Details on mammalian cell type (if applicable):
- Type and identity of media: Modified F12 cell-culture medium
- Metabolic activation:
- with and without
- Metabolic activation system:
- Type and composition of metabolic activation system:
- source of S9 : S9 homogenate from Aroclor 1254 induced rat liver - Test concentrations with justification for top dose:
- 0.1, 0.3, 0.6, 1.0, 1.5, 2.0, 33.0 mg/mL
- Vehicle / solvent:
- water
- Untreated negative controls:
- yes
- Negative solvent / vehicle controls:
- yes
- True negative controls:
- no
- Positive controls:
- yes
- Positive control substance:
- ethylmethanesulphonate
- Remarks:
- without S9 Mix
- Untreated negative controls:
- yes
- Negative solvent / vehicle controls:
- yes
- True negative controls:
- no
- Positive controls:
- yes
- Positive control substance:
- other: dimethylnitrosoamine
- Remarks:
- with S9 mix
- Details on test system and experimental conditions:
- Approximately 20-24 h prior to mutation test, 5 x10E5 cells were inoculated into two 25-cm2 culture flasks containing F12-D5 medium, and incubated at 37°C in a 5% CO2 atmosphere. On the day of testing, appropriate concentrations of the test agent were added to duplicate cultures of cells, and cultures were treated for 5 h at 37°C. The cells were allowed a period of 18-24 h of recovery from treatment before chemical-induced cytotoxicity was determined. Treatment of cells in the presence of an S9 metabolic activation system was performed identically, with the exception that F12 medium without serum was used. The colony-forming potential of 100-200 treated cells was used as measure of treatment-induced cytotoxicity.
At 2- to 3-day intervals after treatment, cells were subcultured. After a period of at least 7 days to allow the expression of the mutant phenotype, cells were dissociated with 0.075% trypsin, counted and plated. The colony-forming ability determined by the viable fraction of the plated cells was used to correct mutant frequency for the individual treated cultures and to detect variations in the growth ability of the cells. - Statistics:
- Statistical analysis of the mutation data for this test been described by Slesinski et al.
- Key result
- Species / strain:
- Chinese hamster Ovary (CHO)
- Metabolic activation:
- with and without
- Genotoxicity:
- negative
- Cytotoxicity / choice of top concentrations:
- no cytotoxicity
- Vehicle controls validity:
- valid
- Untreated negative controls validity:
- valid
- True negative controls validity:
- not examined
- Positive controls validity:
- valid
- Additional information on results:
- While the positive control substances, ethylmethane sulfonate and dimethylnitrosamine, both produced increased mutant frequencies, MDEA treatment did not produce a reproducible dose-related increase in the number of mutants over the range of concentrations tested either with or without an S9 metabolic activation system. Some small and sporadic numerical in creases in the mutation frequencies were observed, these increases were within the historical control variability for this test system and they were statistically different from the concurrent control.
Therefore, MDEA was not considered to be mutagenic in this in vitro gene mutation test. - Endpoint:
- in vitro cytogenicity / chromosome aberration study in mammalian cells
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- test procedure in accordance with national standard methods with acceptable restrictions
- Qualifier:
- equivalent or similar to guideline
- Guideline:
- OECD Guideline 473 (In Vitro Mammalian Chromosome Aberration Test)
- Deviations:
- yes
- Remarks:
- only without metabolic activation tested
- Principles of method if other than guideline:
- Method according to Dean et al.: Mut. Res., 153, 57-77, (1985)
- GLP compliance:
- not specified
- Type of assay:
- in vitro mammalian chromosome aberration test
- Specific details on test material used for the study:
- SOURCE OF TEST MATERIAL
- Source and lot/batch No.of test material: 17589
- Species / strain / cell type:
- hepatocytes:
- Details on mammalian cell type (if applicable):
- Rat -liver cell line RL4 is a epithelial-type cell line derived by Dean et al. following the procedure descibed by Williams et al. 1971. RL4 was derived from a 10 -day old Wistar rat in 1978 (Dean and Hodson-Walker, 1979).
- Metabolic activation:
- without
- Test concentrations with justification for top dose:
- 100 - 400 µg/mL
- Untreated negative controls:
- yes
- Negative solvent / vehicle controls:
- yes
- True negative controls:
- no
- Positive controls:
- yes
- Positive control substance:
- other: see below
- Details on test system and experimental conditions:
- Cultured rat-liver cells were grown on microscope slides contained in petri dishes. Treatment was again for a 24-h period and positive control slides were included. Colcemid was added 2 h before exposure was complete. At exposure completion the cultures were harvested and a hypotonic solution was added to the cell suspension. After the hypotonic treatment the suspension was centrifuged, the solution was decanted and the cells fixed in 3 changes of fixative solution (methanol : acetic acid 3:1). Chromosome preparations were made on microscope slides and stained with Giemsa stain. The preparations were randomly coded and 100 cells from each cultured were analysed microscopically.
Cytotoxicity assay
Monolayer cultures of rat-liver cells were prepared in multi-well tissue culture trays. The cultures were incubated at 37°C for 24 h to commence active growth before treatment with the test compounds. After 24 h exposure the cell monolayers were stained and the growth inhibition effects noted. The concentrations selected for the chromosome assay were 0.5, 0.25 and 0.125 of the concentration at which growth was inhibited to 50 % (GI50). - Key result
- Species / strain:
- other: rat hepatocytes RL4
- Metabolic activation:
- without
- Genotoxicity:
- negative
- Cytotoxicity / choice of top concentrations:
- not specified
- Vehicle controls validity:
- not specified
- Untreated negative controls validity:
- not specified
- Positive controls validity:
- not specified
Referenceopen allclose all
Table 1: Results:
Chemical | TA98 | TA100 | TA1535 | TA1537 | TA1538 | ||||||
Dose (mg/plate) | -S9 | +S9 | -S9 | +S9 | -S9 | +S9 | -S9 | +S9 | -S9 | +S9 | |
water | 100 | 22±5 | 14±5 | 123±24 | 127±27 | 10±2 | 11±2 | 7±2 | 6±2 | 8±2 | 11±4 |
4 -NPD | 0.01 | 683±43 | - | - | - | - | - | - | - | 794±50 | - |
NaN3 | 0.01 | - | - | 1087±60 | - | 917±194 | - | - | - | - | - |
9 -AA | 0.06 | - | - | - | - | - | - | 240±33 | - | - | - |
2 -AA | 0.0025 | - | 1890±34 | - | 1757±164 | - | 123±10 | - | 299±6 | - | 1655±109 |
MDEA | 0.1 | 26±3 | 21±6 | 87±13 | 124±17 | 15±12 | 11±4 | 11±6 | 5±2 | 8±1 | 13±3 |
MDEA | 0.3 | 19±4 | 18±1 | 113±20 | 104±4 | 13±5 | 13±3 | 4±2 | 5±3 | 12±3 | 10±4 |
MDEA | 1 | 18±3 | 19±0 | 106±13 | 102±6 | 10±4 | 11±2 | 6±3 | 5±2 | 8±1 | 13±5 |
MDEA | 3 | 22 (s) | 15±2 | 80±6 | 101±16 | 8 (s) | 5±2 | 4±2 | 4±2 | 7 (T) | 10±4 |
MDEA | 5 | 15±3 | 100±11 | 11±1 | 3±1 | 16±1 | |||||
MDEA | 10 | toxic | toxic | toxic | toxic | toxic |
4-NPD: 4-nitrophenylenediamine;
NaN3: sodium azide;
9-AA: 9-aminoacridine;
2-AA: 2-aminoanthracene.
Toxic: clearing of background lawn or average number of colonies less than half of the solvent control value.
S: sparse growth of background lawn in one or two of the triplicates tested. Counts not included in the calculation of mean and standard deviations not calculated.
T: toxic to one or two of the triplicates tested.
No mutagenic activity was observed in any of the 5 strains mutants over the range of concentrations tested in the absence or the presence of S9 activation, either by evidence of a dose-response relation or a doubling of the mean number of colonies over the vehicle control value.
Endpoint conclusion
- Endpoint conclusion:
- no adverse effect observed (negative)
Genetic toxicity in vivo
Description of key information
MDEA was evaluated for potential genotoxic activity in an in vivo peripheral blood micronucleus test in Swiss-Webster mice (similar to OECD 474, no GLP). MDEA did not produce any significant or dose-related increases in the frequencies of micronuclei.
Link to relevant study records
- Endpoint:
- in vivo mammalian somatic cell study: cytogenicity / erythrocyte micronucleus
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- study well documented, meets generally accepted scientific principles, acceptable for assessment
- Qualifier:
- equivalent or similar to guideline
- Guideline:
- OECD Guideline 474 (Mammalian Erythrocyte Micronucleus Test)
- Principles of method if other than guideline:
- Method according to Schmid (1975) and McGregor (1980)
- GLP compliance:
- not specified
- Type of assay:
- mammalian erythrocyte micronucleus test
- Species:
- mouse
- Strain:
- Swiss Webster
- Sex:
- male/female
- Details on test animals or test system and environmental conditions:
- TEST ANIMALS
- Age at study initiation: 6-8 weeks - Route of administration:
- intraperitoneal
- Duration of treatment / exposure:
- single application
- Frequency of treatment:
- once
- Post exposure period:
- 30, 48 and 72 hours
- Dose / conc.:
- 175 mg/kg bw/day (nominal)
- Dose / conc.:
- 350 mg/kg bw/day (nominal)
- Dose / conc.:
- 560 mg/kg bw/day (nominal)
- No. of animals per sex per dose:
- 5
- Control animals:
- yes, concurrent vehicle
- Positive control(s):
- triethylenemelamine
- Route of administration: i.p.
- Doses / concentrations: 0.3 mg/kg
- 30 h post dosing - Tissues and cell types examined:
- peripheral blood erythrocytes
- Details of tissue and slide preparation:
- CRITERIA FOR DOSE SELECTION:
based on pretest: about 80, 50 and 25 % of the LD50
DETAILS OF SLIDE PREPARATION:
Slides of blood smears were stained with Gurr's R-66 Giemsa diluted in phosphate buffer, coded and read without knowledge of treatment group to prevent bias.
METHOD OF ANALYSIS:
The polychromatic/normochromatic erythrocyte ratio for approximately 1000 total cells for each animal was calculated to provide an estimate of cytotoxicity.
- Evaluation criteria:
- A positive result was concluded if at least one statistical significant increase above vehicle control was an indication of a dose-related effect.
- Statistics:
- Data were compared for significant differences using the Fisher's Exact Test.
- Key result
- Sex:
- male/female
- Genotoxicity:
- negative
- Toxicity:
- no effects
- Vehicle controls validity:
- valid
- Negative controls validity:
- valid
- Positive controls validity:
- valid
- Additional information on results:
- There were no significant differences in the polychromatic erythrocyte to normochromatic erythrocyte ratios at any dosage. Furthermore, no significant increases in the incidence of micronucleated polychromatic erythrocyte were observed at any sampling time. Therefore, MDEA is not considered to be inducer of micronuclei under the condition of this in vivo test.
Reference
Induction of micronucleus in peripheral erythrocytes:
Sex | Mean PCE/1000 NCE (±SD) | ||||
Water | TEM | MDEA (mg/kg) | |||
175 | 350 | 560 | |||
30 h postdosing | |||||
Male | 52±24 | 36±8 | 55±17 | 64±11 | 70±12 |
Female | 35±10 | 36±9 | 41±8 | 48±9 | 41±14 |
48 h postdosing | |||||
Male | 43±13 | 45±17 | 43±12 | 36±4 | |
Female | 31±6 | 34±18 | 32±12 | 38±4 | |
72 h postdosing | |||||
Male | 39±7 | 38±12 | 36±14 | 32±14 | |
Female | 32±9 | 31±11 | 39±9 | 24±7 |
Sex | Mean MN-PCE/1000 NCE (±SD) | ||||
Water | TEM | MDEA (mg/kg) | |||
175 | 350 | 560 | |||
30 h postdosing | |||||
Male | 5.4±3.2 | 42.0±8 b | 4.8±2.4 | 6.6±2.9 | 4.8±3.5 |
Female | 2.6±1.7 | 43±15 b | 4.2±2.8 | 3.0±0.7 | 1.6±1.5 |
48 h postdosing | |||||
Male | 3.8±3.1 | 4.2±2.8 | 5.0±4.4 | 3.0±2.0 | |
Female | 2.4±1.5 | 3.8±2.4 | 2.2±1.3 | 2.6±2.7 | |
72 h postdosing | |||||
Male | 5.0±2.0 | 2.6±2.1 | 7.0±5.6 | 2.7±1.2 | |
Female | 3.2±1.1 | 2.2±1.3 | 3.0±2.8 | 2.8±1.9 |
There were no significant differences in the polychromatic erythrocyte to normochromatic erythrocyte ratios at any dosage. Furthermore, no significant increases in the incidence of micronucleated polychromatic erythrocyte were observed at any sampling time. Therefore, MDEA is not considered to be inducer of micronuclei under the condition of this in vivo test.
Endpoint conclusion
- Endpoint conclusion:
- no adverse effect observed (negative)
Additional information
In vitro
MDEA was evaluated for mutagenicity at concentrations of 0.1, 0.3, 1, 3, 5, and 10 mg/plate in the Salmonella/microsome reverse gene mutation test (similar to OECD 471, no GLP). The strains tested were S. typhimurium TA98, TA100, TA1535, TA1537 and TA1538. Cytotoxicity was observed from 3 mg/plate onwards in absence of S9 mix, and at 10 mg/plate in presence of S9 mix. No mutagenic activity was observed in any of the 5 strains tested in the absence or the presence of S9 activation, either by evidence of a dose-response relationship or a doubling of the mean number of colonies over the vehicle control value. MDEA was therefore considered not mutagenic under the conditions of this in vitro mutagenicity test (Leung & Ballantyne, 1997).
In another Ames test (also similar the OECD 471), MDEA was tested in S. typhimurium TA 1535, TA 1537, TA 98 and TA 100 (with and without metabolic activation) using concentrations of 33, 100, 333, 1000, 2000, 3333 and 10000 µg/plate (Zeiger et al, 1987). No mutagenic effects were observed. Cytotoxicity was observed from 3333 µg/plate.
In a CHO/HGPRT forward gene mutation test (similar to OECD 476, no GLP), MDEA treatment (0.1, 0.3, 0.6, 1.0, 1.5, 2.0, 33.0 mg/mL) did not produce a reproducible dose-related increase in the number of mutants over the range of concentrations tested either with or without an S9 metabolic activation system. Cytotoxicity was not observed. MDEA was not considered to be mutagenic in this in vitro gene mutation test (Leung & Ballantyne, 1997).
In a SCE test (similar to OECD 479, no GLP), statistically significant increases in the mean number of SCEs were observed in one culture at 0.3 mg/mL MDEA, and in duplicate cultures at 0.6 and 1.0 mg/mL MDEA in the absence of S9 metabolic activation. These increases were small, being less than 1.5-fold those of untreated controls, and they were not dose-related. In the presence of S9 metabolic activation, MDEA failed to produce any statistically significant increase in SCEs in comparison to concurrent controls. There were no increases in the numbers of first division cells which suggests that the dose ranges used were appropriate. Therefore, MDEA was not considered to induce reciprocal chromatid exchanges under the condition of this in vitro test (Leung & Ballantyne, 1997).
No chromosome aberration assay is available for MDEA. Therefore, read-across to the structural analogous substance MEA was performed. MEA is negative in a chromosome aberration test in rat hepatocytes, performed according to the protocol similar to OECD guideline 473, at concentrations 100-400 μg/mL in the absence of metabolic activation (Dean et al., 1985).
In vivo
In the mouse micronucleus test (similar to OECD 474, no GLP), mice were dosed by a single intraperitoneal injection and observed for mortality for 72 h. Three dose levels of 175, 350, and 560 mg/kg bw (about 25, 50 and 80% of the LD50) were selected for the micronucleus test. There were no major gender differences in mortality responses. The LD50 (combined sexes) for MDEA was about 696 mg/kg bw. Selection of the top test dose was based on the lethality response rather than on bone marrow suppression. There were no significant differences in the polychromatic erythrocyte to normochromatic erythrocyte ratios at any dosages. Furthermore, no significant increases in the incidence of micronucleated polychromatic erythrocyte were observed at any sampling time. Therefore, MDEA was not considered to be an inducer of micronuclei under the conditions of this in vivo test (Leung & Ballantyne, 1997).
Justification for classification or non-classification
Classification,
Labelling, and Packaging Regulation (EC) No 1272/2008
The
available information on the test item regarding genetic toxicity are
reliable and suitable for classification purposes under Regulation (EC)
No 1272/2008. Based on available experimental information, the
test substance is not classified for genetic toxicity according
to Regulation (EC) No 1272/2008 (CLP), as amended for the tenth time in
Regulation (EU) No 2017/776.
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