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EC number: 411-950-4 | CAS number: 96562-58-2 DHPPME; MAK-ME; MEHPOPS; R-MAQ-ME
- 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
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Study period:
- 12 November 1992 to 07 December 1992
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- guideline study
Data source
Reference
- Reference Type:
- study report
- Title:
- Unnamed
- Year:
- 1 993
- Report date:
- 1993
Materials and methods
Test guidelineopen allclose all
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 474 (Mammalian Erythrocyte Micronucleus Test)
- Version / remarks:
- 1983
- Deviations:
- yes
- Remarks:
- see below
- Qualifier:
- according to guideline
- Guideline:
- EU Method B.12 (Mutagenicity - In Vivo Mammalian Erythrocyte Micronucleus Test)
- Version / remarks:
- 1984
- Deviations:
- yes
- Remarks:
- see below
- Principles of method if other than guideline:
- The limit dose of 2000 mg/kg, promulgated by the OECD and subsequently ratified in 92/49/EEC after the release of the guidelines, was used.
- GLP compliance:
- yes
- Type of assay:
- other: Mouse micronucleus test
Test material
- Reference substance name:
- Methyl (R)-2-(4-hydroxyphenoxy)propionate
- EC Number:
- 411-950-4
- EC Name:
- Methyl (R)-2-(4-hydroxyphenoxy)propionate
- Cas Number:
- 96562-58-2
- Molecular formula:
- C10H12O4
- IUPAC Name:
- methyl (2R)-2-(4-hydroxyphenoxy)propanoate
- Test material form:
- solid
- Details on test material:
- - Appearance: Tan or brown solid
- Storage conditions: In the dark at ambient temperature
Constituent 1
Test animals
- Species:
- mouse
- Strain:
- Swiss
- Remarks:
- OF1 strain
- Sex:
- male/female
- Details on test animals or test system and environmental conditions:
- TEST ANIMALS
- Age at study initiation: Approximately 6 weeks old
- Weight at study initiation: Mean body weight of 29.2 to 33.4 g for the males and 24.4 to 30.0 g for the females
- Assigned to test groups randomly: Yes, allocated randomly to groups according to sex
- Fasting period before study: No
- Housing: The animals were housed in polycarbonate cages (33.5 x 18.7 x 13.0 cm) and each cage contained 5 mice of the same sex and group (3 for the supplementary animals). Each cage contained autoclaved sawdust.
- Diet: ad libitum pelleted diet
- Water: ad libitum access to filtered tap water contained in bottles
- Acclimation period: 5 day acclimation period
ENVIRONMENTAL CONDITIONS
- Temperature: 21 ± 2 °C
- Humidity: 50 ± 20 % (relative)
- Air changes: Ventilation was provided in the form of filtered and non-recycled fresh air
- Photoperiod: 12 h/12 h light/dark cycle
IN-LIFE DATES
- From: 12 November 1992
- To: 19 November 1992
Administration / exposure
- Route of administration:
- oral: gavage
- Vehicle:
- - Vehicle(s)/solvent(s) used: 1 % aqueous hydrogel of methylcellulose
- Justification for choice of solvent/vehicle: Not specified
- Concentration of test material in vehicle: 100 mg/mL
- Dose volume: 20 mL/kg
- Lot/batch no. of vehicle: 92126 provided by Prolabo, Paris - Details on exposure:
- PREPARATION OF DOSING SOLUTIONS: The test material was suspended in the vehicle at a concentration of 100 mg/mL and homogenised using a magnetic stirrer before and during administration. The preparations were made immediately before use.
- Duration of treatment / exposure:
- Animals were sacrificed either after 24 or 48 hours following treatment with the test material and vehicle control. Animals were sacrificed 24 hours after treatment with the positive control.
- Frequency of treatment:
- Single administration
Doses / concentrations
- Dose / conc.:
- 2 000 mg/kg bw/day (nominal)
- No. of animals per sex per dose:
- Two groups each consisting of 5 males and 5 females were treated with the test material at 2000 mg/kg. An additional group of 3 males and 3 females was also treated with the test material at 2000 mg/kg.
- Control animals:
- yes, concurrent vehicle
- Positive control(s):
- Cyclophosphamide was used as the positive control
- Route of administration: Oral gavage
- Doses / concentrations: 50 mg/kg dosed at a concentration of 2.5 mg/mL
- Preparation: The test material was dissolved in distilled water immediately before use
Examinations
- Tissues and cell types examined:
- Bone marrow smears prepared from the femurs of the mice
- Details of tissue and slide preparation:
- PREPARATION OF SMEARS
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 foetal 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.
ANALYSIS
All slides were scored under a high powered microscope (x 1000). For each animal, the micronuclei were counted in 2000 polychromatic erythrocytes; the polychromatic (PE) and normochromatic (NE) erythrocyte ratio was established by scoring a total of 1000 erythrocytes (PE + NE). - Evaluation criteria:
- The following criteria were used as an aid for determining a positive response:
- A statistically significant increase in the number of MPE for at least one of the sampling times when compared to the vehicle group;
- This increase should double the number of MPE for the historical data.
The results were considered negative if the above criteria were not fully met. - Statistics:
- At each sampling 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 chi-squared test;
- For the PE/NE ratio, the Student's "t" test, in which p = 0.05 was used as the lowest level of significance.
Biological and statistical significances were considered during the evaluation.
Results and discussion
Test results
- Key result
- Sex:
- male/female
- Genotoxicity:
- negative
- Toxicity:
- no effects
- Vehicle controls validity:
- valid
- Negative controls validity:
- not examined
- Positive controls validity:
- valid
- Additional information on results:
- RESULTS OF RANGE-FINDING STUDY
The administration of 2000 mg/kg induced no mortality and no clinical signs. Consequently, 2000 mg/kg, being the maximum dose specified in the guidelines, was selected for the cytogenetic study.
RESULTS OF DEFINITIVE STUDY
No clinical signs and no mortality were observed after treatment with the test material. The MPE and PE/NE ratio data are summarised Table 1. In the 2 vehicle control groups, the mean values of micronucleated polychromatic erythrocytes were within the range of the historical data. In all groups treated with the test material, the mean values of micronucleated polychromatic erythrocytes were similar to those of their respective vehicle groups at each sampling time, and no statistically significant differences were observed. Moreover, the PE/NE ratio was not statistically significantly different from that of the respective vehicle control groups. As no mortality occurred in the study, the supplementary animals were not needed and no smears were prepared for these animals.
The treatment with CPA induced a statistically significant increase (p<0.001) in the number of MPE, which demonstrated the sensitivity of this in vivo test under the experimental conditions.
Any other information on results incl. tables
Table 1: Summary of MPE and PE/NE ratio data
Group |
Dose (mg/kg) |
MPE/PE |
PE/NE Ratio |
Time of sacrifice (hours) |
||
Mean |
SD |
Mean |
SD |
|||
Vehicle |
- |
1.5 |
1.0 |
0.6 |
0.2 |
24 |
Test Material |
2000 |
2.4 |
1.2 |
0.7 |
0.3 |
|
Positive Control |
50 |
43.1*** |
7.1 |
0.9 |
0.5 |
|
Vehicle |
- |
1.2 |
0.7 |
0.7 |
0.2 |
48 |
Test Material |
2000 |
1.0 |
0.6 |
0.7 |
0.2 |
Five animals per sex per group
PE = polychromatic erythrocytes
NE = normochromatic erythrocytes
MPE /PE = micronucleated polychromatic erythrocytes / 1000 polychromatic erythrocytes
SD = standard deviation
***p<0.001
Applicant's summary and conclusion
- Conclusions:
- Under the conditions of the study, the test material did not induce cytogenetic damage to the bone marrow cells of mice when treated by the oral route at 2000 mg/kg in the micronucleus test.
- Executive summary:
The potential for the test material to induce cytogenetic damage to the bone marrow cells of mice was investigated in accordance with the standardised guidelines OECD 474 and EU method B12 under GLP conditions.
Following a preliminary study to define the dose to be used, the animals of the treated groups received a single administration of the test material at the limit dose of 2000 mg/kg by oral gavage. Two groups each comprising 5 males and 5 females (and one additional group composed of 3 males and 3 females) were dosed. The vehicle was 1 % aqueous methylcellulose and 2 vehicle groups were also treated. The animals of the positive control group (1 group, comprising 5 males and 5 females) received a single administration of cyclophosphamide at 50 mg/kg.
The animals of the treated and vehicle control groups were sacrificed 24 and 48 hours after treatment and the animals of the positive control group were sacrificed 24 hours after treatment. Bone marrow smears were then prepared.
For each animal, the micronuclei were counted in 2000 polychromatic erythrocytes. The polychromatic (PE) and normochromatic (NE) erythrocyte ratio was established by scoring a total of 1000 erythrocytes (PE + NE).
There were no clinical signs of toxicity after treatment with the test material. At the two sampling times, the number of MPE and the PE/NE ratio in mice exposed to the test material did not differ statistically from the concurrent vehicle control values. As no mortality occurred in the study, the supplementary animals were not needed and no smears were prepared for these animals.
In the two vehicle control groups, the mean values of micronucleated polychromatic erythrocytes (MPE) were within the range of the historical data. Cyclophosphamide induced a highly significant increase (p<0.001) in MPE, indicating the sensitivity of the test system under the experimental conditions.
Under the conditions of the study, the test material did not induce cytogenetic damage to the bone marrow cells of mice when treated by the oral route at 2000 mg/kg in the micronucleus test.
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