Registration Dossier
Registration Dossier
Data platform availability banner - registered substances factsheets
Please be aware that this old REACH registration data factsheet is no longer maintained; it remains frozen as of 19th May 2023.
The new ECHA CHEM database has been released by ECHA, and it now contains all REACH registration data. There are more details on the transition of ECHA's published data to ECHA CHEM here.
Diss Factsheets
Use of this information is subject to copyright laws and may require the permission of the owner of the information, as described in the ECHA Legal Notice.
EC number: 692-614-6 | CAS number: 5660-53-7
- 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:
- migrated information: read-across from supporting substance (structural analogue or surrogate)
- Adequacy of study:
- key study
- Study period:
- From 15 May 2009 to 30 September 2009
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- other: see 'Remark'
- Remarks:
- The study was performed on the analogue substance 2,2-Dimethyl-1,3-dioxolane-4-methanol (for justification of read-across between the registered substance and its analogue, please refer to corresponding assessment report in Section 13). The study was GLP compliant and performed according to OECD guideline 474 without any deviations.
Cross-referenceopen allclose all
- Reason / purpose for cross-reference:
- reference to same study
- Reason / purpose for cross-reference:
- reference to other study
Data source
Reference
- Reference Type:
- study report
- Title:
- Unnamed
- Year:
- 2 009
- Report date:
- 2009
Materials and methods
Test guideline
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 474 (Mammalian Erythrocyte Micronucleus Test)
- Deviations:
- no
- Principles of method if other than guideline:
- Not applicable
- GLP compliance:
- yes (incl. QA statement)
- Remarks:
- 19 November 2008
- Type of assay:
- micronucleus assay
Test material
- Reference substance name:
- 2,2-Dimethyl-1,3-dioxolane-4-methanol
- IUPAC Name:
- 2,2-Dimethyl-1,3-dioxolane-4-methanol
- Reference substance name:
- 2,2-dimethyl-1,3-dioxolan-4-ylmethanol
- EC Number:
- 202-888-7
- EC Name:
- 2,2-dimethyl-1,3-dioxolan-4-ylmethanol
- Cas Number:
- 100-79-8
- Molecular formula:
- C6H12O3
- IUPAC Name:
- (2,2-dimethyl-1,3-dioxolan-4-yl)methanol
- Test material form:
- other: liquid
- Details on test material:
- - Name of test material (as cited in study report): PEX-01; 2,2-Dimetil-4-Hidroximetil-1,3-
Dioxolano
- Physical state: Clear liquid
- Analytical purity: 99.5%
- pH of test substance = 6
- Composition of test material, percentage of components: 99.9% 2,2-Dimethyl-1,3-dioxolane-4-methanol; water: 0.02%; Acidity (Acetic acid): 0.0021%
- Lot/batch No.: 081001
- Expiration date of the lot/batch: 01 October 2009
- Stability under test conditions: Stable at room temperature and under normal conditions of use
- Storage condition of test material: at room temperature
Constituent 1
Constituent 2
Test animals
- Species:
- mouse
- Strain:
- Swiss
- Sex:
- male
- Details on test animals or test system and environmental conditions:
- TEST ANIMALS
- Source: Paulistec, Mairiporã - SP
- Weight at study initiation: no data
- Age at study initiation: 9 weeks
- Assigned to test groups randomly: no data
- Housing: Animals were housed in polypropylene cages measuring 30 x 20 x 13 cm, with six animals per cage.
- Diet: Pelleted commercial diet (Biobase Biotec, batch R10/09), ad libitum
- Water: Filtered water, ad libitum
- Acclimation period: 5 days
ENVIRONMENTAL CONDITIONS
- Temperature: 20 to 22 °C
- Humidity: 70 %
- Ventilation: no data
- Photoperiod: 12 h dark / 12 h light
IN-LIFE DATES: From: 19 August 2009 To: 21 August 2009
Administration / exposure
- Route of administration:
- intraperitoneal
- Vehicle:
- - Vehicle(s)/solvent(s) used: Deionized water
- Concentration of test material in vehicle: no data
- Stability in vehicle: no data - Details on exposure:
- PREPARATION OF DOSING SOLUTIONS:
- Test item was dissolved in deionized water.
DOSE VOLUME: 5 mL/kg bw - Duration of treatment / exposure:
- - Vehicle control, positive control and treated groups: Two consecutive days treatment at 24 h interval
- Frequency of treatment:
- - Vehicle control and treated groups: Once daily for two days
- Post exposure period:
- Vehicle control, positive control and treated groups: from 18 to 24 h after the second treatment
Doses / concentrations
- Remarks:
- Doses / Concentrations:
Preliminary test assay: : 2000 mg/kg bw/day Main assay: 2000 mg/kg bw/day
Basis:
nominal conc.
- No. of animals per sex per dose:
- Preliminary toxicity assay: 5 animals (2 in a first assay, 3 others to confirm the observations)
Main assay:
- Negative and positive control group: 6 animals/group
- Treated group-2000 mg/kg bw/day: 6 animals - Control animals:
- yes, concurrent vehicle
- Positive control(s):
- Cyclophosphamide
- Route of administration: Intraperitoneal route
- Dose: 50 mg/kg bw
- Dose volume: 5 mL/kg bw
Examinations
- Tissues and cell types examined:
- - Polychromatic (PCE) and normochromatic (NCE) erythrocyte ratio was established by scoring a total of 1500 erythrocytes (PCE+NCE) per animal.
- For each animal, the micronucleated PCE (MNPCE) were counted in 3000 PCE. - Details of tissue and slide preparation:
- CRITERIA FOR DOSE SELECTION:
- Dose levels were selected on the basis of results of preliminary toxicity assay in which the test item was administered by intraperitoneal injection to Swiss mice at the dose of 2000 mg/kg bw/day for two consecutive days at 24 h interval.
TREATMENT AND SAMPLING TIMES:
- Two consecutive treatments at 24 h interval followed by sacrificing the animals 18 to 24 h after second treatment (vehicle control, positive control and treatment groups)
DETAILS OF SLIDE PREPARATION:
- At the sampling time, all the animals were sacrificed.
- Femurs of the mice were removed and the bone marrow was extracted with foetal calf serum.
- After centrifugation and re-suspension in a small volume of foetal calf serum, bone marrow smears were prepared in glass slides.
- Slides were air-dried, fixed, stained using Wright-Giemsa and blind evaluated using an optical microscope. - Evaluation criteria:
- - Micronuclei are uniform, darkly stained, more or less round bodies in the cytoplasm of erythrocytes. Inclusions which are reflective, improperly shaped or stained, or which are not in the focal plan of the call are judged to be artifacts and are not scored as micronuclei. Cells containing more than one micronucleus are only counted once.
- Positive and negative controls were compared to ensure that the assay was performed according to the prescribed standards.
- A test substance is considered to be active in the test system if there is a clear dose-related increase in the micronuclei frequency compared to negative control at any tested dose.
- Historical negative control data from the laboratory may also be used for comparison between groups.
- The biological relevance of the results was considered together with the statistical significance to evaluate the effects. - Statistics:
- - A modified shi-square test according to Pereira (1991) was employed for analysis of the results.
Results and discussion
Test results
- Sex:
- male
- Genotoxicity:
- negative
- Toxicity:
- yes
- Remarks:
- Mild transient ataxia
- Vehicle controls validity:
- valid
- Negative controls validity:
- not applicable
- Positive controls validity:
- valid
- Additional information on results:
- RESULTS OF PRELIMINARY TOXICITY ASSAY
- Dose: 2000 mg/kg bw/day for two consecutive days at 24 h interval.
- Mortality: No mortality was observed.
- Clinical signs: All the treated-animals presented mild ataxia after the applications on days 1 and 2 with complete reversion one hour after each injection. The highest dose level which did not produce severe toxicity or lethality was 2000 mg/kg bw. No clinical signs were observed in animals of the negative and positive control groups.
RESULTS OF MAIN ASSAY
Induction of micronuclei (for Micronucleus assay):
- The positive control group treated with cyclophosphamide induced a highly significant increase in the frequency of micronuclei indicating sensitivity of the test system (388 micronuclei were observed in the 18000 PCE).
- In the vehicle control group, the results were consistent to the historical data.
- When animals treated with the test item were compared to the concurrent negative control group, a lower number of micronucleated PCE was observed in the treated group. While 15 micronuclei were observed in the 18000 PCE of the negative control group, 11 micronuclei were observed in the 18000 PCE of the group test with 2000 mg/kg bw of the test item. For this reason, chi-square test was not necessary for comparison between negative control and experimental group.
- See table 7.6.2/1
Ratio of PCE/NCE (for Micronucleus assay):
Six animals were analyzed in the experimental and control groups. A total of 18000 cells were analyzed per group. The quality of the slides allowed a clear differentiation between PCE and NCE. Analysis of the cells showed an approximate 1:1 PCE/NCE rate indicating that there was not a very highly toxic effect of the test substance in the bone marrow of the treated animals
HISTORICAL DATA
- Results were compared with the historical data of the laboratory.
Any other information on results incl. tables
Table 7.6.2/1: Results of micronucleus assay
Dose |
PCE/NCE ratio |
MNPCE |
|
Number |
% |
||
Vehicle |
1.05 |
2 |
0.07 |
1.14 |
3 |
0.10 |
|
1.04 |
2 |
0.07 |
|
0.92 |
2 |
0.07 |
|
1.15 |
2 |
0.07 |
|
1.01 |
4 |
0.13 |
|
Test item 2000 mg/kg bw/day |
1.01 |
2 |
0.07 |
1.12 |
2 |
0.07 |
|
0.99 |
1 |
0.03 |
|
1.08 |
2 |
0.07 |
|
1.05 |
2 |
0.07 |
|
1.12 |
2 |
0.07 |
|
Cyclophosphamide 50 mg/kg bw |
0.83 |
70 |
2.33 |
0.83 |
65 |
2.17 |
|
0.75 |
66 |
2.20 |
|
0.75 |
59 |
1.97 |
|
0.83 |
65 |
2.17 |
|
0.75 |
63 |
2.10 |
Applicant's summary and conclusion
- Conclusions:
- Interpretation of results (migrated information): negative
Under the test conditions, PEX-01 was not clastogenic and not aneugenic in bone marrow cells of mice. - Executive summary:
In an in vivo bone marrow micronucleus assay performed according to OECD Guideline 474 and in compliance with GLP, Swiss male mice (6/group) were administered 2,2-Dimethyl-1,3-dioxolane-4-methanol in distilled water by intraperitoneal injections at the dose level of 2000 mg/kg bw/day with 2 consecutive treatments at 24 h interval. The vehicle and positive control groups (6 animals/group) received distilled water and cyclophosphamide at 50 mg/kg bw, respectively. Bone marrow smears were obtained from treatment, vehicle and positive control groups approximately 24 h after last administration. Polychromatic (PCE) and normochromatic (NCE) erythrocyte ratio was established by scoring a total of 1500 erythrocytes. For each animal, the micronuclei were counted in 3000 polychromatic erythrocytes. A preliminary toxicity study on two animals was conducted before the main study at the dose of 2000 mg/kg bw/day for two consecutive days and was confirmed on three other animals.
When animals treated with the test item were compared to the concurrent negative control group, a lower number of micronucleated PCE was observed in the treated group. For this reason, statistical analysis by chi-square test was not necessary for comparison between negative control and experimental group. Positive control induced a statistically significant increase in micronucleated polychromatic erythrocytes indicating the validity of the study.
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.