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EC number: 220-688-8 | CAS number: 2867-47-2
- 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 vivo
Administrative data
- Endpoint:
- in vivo mammalian somatic cell study: cytogenicity / erythrocyte micronucleus
- Remarks:
- Type of genotoxicity: chromosome aberration
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- guideline study
- Remarks:
- GLP.
Data source
Referenceopen allclose all
- Reference Type:
- study report
- Title:
- Unnamed
- Year:
- 1 993
- Report date:
- 1993
- Reference Type:
- secondary source
- Title:
- Atochem (1993), Micronucleus test in Mice, CIT 9776 MAS
- Author:
- Atochem
- Year:
- 2 003
- Bibliographic source:
- cited in: OECD SIDS, 2-Dimethylaminoethylmethacrylate, CAS No: 2867-47-2, 07/2003
Materials and methods
Test guideline
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 474 (Mammalian Erythrocyte Micronucleus Test)
- GLP compliance:
- yes
- Type of assay:
- micronucleus assay
Test material
- Reference substance name:
- 2-dimethylaminoethyl methacrylate
- EC Number:
- 220-688-8
- EC Name:
- 2-dimethylaminoethyl methacrylate
- Cas Number:
- 2867-47-2
- Molecular formula:
- C8H15NO2
- IUPAC Name:
- 2-(dimethylamino)ethyl methacrylate
- Test material form:
- liquid
Constituent 1
- Specific details on test material used for the study:
- TEST MATERIAL:
- Name of test material (as cited in study report): Dimethylaminoethyl methacrylate (MADAME)
Test animals
- Species:
- mouse
- Strain:
- Swiss
- Sex:
- male/female
- Details on test animals or test system and environmental conditions:
- TEST ANIMALS
-Strain: OF1/ICO: OF1 (IOPS Caw)
- Source: Iffa Crédo (69210 L'Arbresle, France)
- Age at study initiation: approx. 6 weeks
- Weight at study initiation: males 21-36 g, females 24-29 g
- Housing: in polycarbonate cages (33.5 X 18.7 X 13.0 cm) and each cage contained 5 mice of the same sex and group
- Diet: A04 C pelleted diet (U.A.R., 91360 Villemoisson-sur-Orge, France) ad libitum
- Water: filtered tap water ad libitum
- Acclimation period: 5 days
ENVIRONMENTAL CONDITIONS
- Temperature (°C): 21±2
- Humidity (%): 50±20
- Photoperiod (hrs dark / hrs light): 12 / 12
Administration / exposure
- Route of administration:
- intraperitoneal
- Vehicle:
- Physiological solution of 0.9% NaCl
- Details on exposure:
- - Application volume: 10 ml/kg bw
- Duration of treatment / exposure:
- Sampling time 14 or 48 hours after second administration.
- Frequency of treatment:
- 2 administrations separated by 24 hrs
Doses / concentrations
- Remarks:
- Doses / Concentrations:
200 mg/kg bw
Basis:
- No. of animals per sex per dose:
- 5
- Control animals:
- yes, concurrent vehicle
- Positive control(s):
- 25 mg/kg bw cyclophosphamide (2 i.p. injections)
Examinations
- Tissues and cell types examined:
- Bone marrow smeares were prepared 24 and 48 hrs after the 2nd administration. The presence of micronuclei was analysed in 2000 polychromatic erythrocytes (PE) per mouse, and the PE/NE ratio was determined.
- Details of tissue and slide preparation:
- At the time of sacrifice, all the animals were sacrificed after CO2 inhalation in excess. The femurs of the mice were removed and the bone marrow eluted out using fetal calf serum. After centrifugation, the supernatant was removed and the cells in the sediment were suspended by shaking. A drop of this cell suspension was placed and spread on a slide. The slides were air-dried and stained with May-Grünwald-Giemsa. Two slides/animal were prepared, but only one was used for scoring. All the slides were coded for scoring.
- Evaluation criteria:
- The following criteria were used as an aid for deterrnining a positive response:
- a statisticaliy significant increase in the number of MPE for at least one of the sampling times when cornpared to the vehicle group,
- this increase should double the number of MPE of our historical data.
The results were considered negative if the above criteria were not fully met. - Statistics:
- At each sarnpling time, the mean number of micronucleated polychromatic erythrocytes (MPE) and the PE/NE ratio from the treated groups were compared to the simultaneous vehicle groups. The intergroup comparison was performed using for MPE, the X² test, and for the PE/NE ratio, the Student's "t" test, in which p = 0.05 was used as the lowest level of significance.
Results and discussion
Test results
- Sex:
- male/female
- Genotoxicity:
- negative
- Toxicity:
- no effects
- Remarks:
- cytotoxicity
- Additional information on results:
- In all groups treated with the TS, the mean values of micronucleated polychromatic erythrocytes were similar to those of their respective vehicle control groups at each sampling time, and no statiscally significant differences were observed. The PE/NE ratio did not differ from that of the respective vehicle control group.
Any other information on results incl. tables
Summary of the test results:
Group |
Dose (mg/kg bw) |
MPE/PE |
PE/NE ratio |
||
Mean |
SD |
Mean |
SD |
||
Time of sacrifice: 24 hours after the 2ndadministration |
|||||
Vehicle |
- |
2.0 |
0.8 |
0.7 |
0.2 |
Test substance |
200 |
1.9 |
1.1 |
0.6 |
0.2 |
CPA |
25 |
18.2*** |
3.8 |
0.4*** |
0.1 |
|
|||||
Time of sacrifice: 48 hours after the 2ndadministration |
|||||
Vehicle |
- |
1.9 |
0.8 |
0.9 |
0.4 |
Test substance |
200 |
1.7 |
1.0 |
1.2 |
0.6 |
*** = P<0.001
Vehicle: physiological solution (0.9% NaCl)
CPA: cyclophosphamide
PE: polychromatic erythrocytes
NE: normochromatic erythrocytes
MPE/PE: micronucleated polychromatic erythrocytes/2000 polychromatic erythrocytes
SD: standard deviation
Applicant's summary and conclusion
- Conclusions:
- Interpretation of results (migrated information): negative
The TS did not induce cytogenetic damage to the bone marrow cells of mice when treated twice separated by 24 hrs by intraperioneal route at 200
mg/kg in the micronucleus test. - Executive summary:
The study was performed according to OECD TD 473 in compliance with GLP.
Swiss OF1/ICO:OF1 IFFA-CREDO mice (5 males and 5 females per group) received two administrations separated by 24 hrs of 200 mg/kg bw TS by the intraperitoneal route. The application of the vehicle (0.9% NaCl solution) served as negative control, cyclophosphamide at 25 mg/kg bw (two-times i.p. injection) served as the positive control. The test animals were killed 24 or 48 hrs after the 2nd administration and bone marrow smears were examined for the presence of micronuclei in 2000 polychromatic erythrocytes (PE) per mouse and for the PE/NE ratio. The number of micronucleated polychromatic cells (MPE) in the dosed animals was not significantly different from that of the animals in the control groups. The PE/NE ratio did not differ from that of the respective vehicle control group.
Conclusion: The TS did not induce cytogenetic damage to the bone marrow cells of mice when treated twice separated by 24 hrs by intraperioneal route at 200 mg/kg in the micronucleus test.
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