Registration Dossier
Registration Dossier
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: 203-962-1 | CAS number: 112-35-6
- 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
- Study period:
- 1990
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- test procedure in accordance with national standard methods
- Remarks:
- Well reported guideline study.
Data source
Reference
- Reference Type:
- study report
- Title:
- Unnamed
- Year:
- 1 990
- Report date:
- 1990
Materials and methods
Test guideline
- Qualifier:
- according to guideline
- Guideline:
- EPA OTS 798.5395 (In Vivo Mammalian Cytogenics Tests: Erythrocyte Micronucleus Assay)
- Deviations:
- no
- GLP compliance:
- yes (incl. QA statement)
- Type of assay:
- micronucleus assay
Test material
- Reference substance name:
- 2-(2-(2-methoxyethoxy)ethoxy)ethanol
- EC Number:
- 203-962-1
- EC Name:
- 2-(2-(2-methoxyethoxy)ethoxy)ethanol
- Cas Number:
- 112-35-6
- Molecular formula:
- C7H16O4
- IUPAC Name:
- 2-[2-(2-methoxyethoxy)ethoxy]ethan-1-ol
- Details on test material:
- - Name of test material (as cited in study report): Triethylene glycol monomethyl ether (TGME)
- Molecular formula (if other than submission substance): CH3-O-C2H4-O-C2H4-O-C2H4-OH
- Molecular weight (if other than submission substance): 162
- Physical state: Liquid
- Analytical purity: 99.23%
- Lot/batch No.: 1-BBF-48-10
- Supplier: Union Carbide Chemicals & Plastic Company Inc.
Constituent 1
Test animals
- Species:
- mouse
- Strain:
- CD-1
- Sex:
- male/female
- Details on test animals or test system and environmental conditions:
- TEST ANIMALS
- Source: Charles River Laboratories, Inc., Wilmington, MA.
- Age at study initiation: 8 weeks old
- Assigned to test groups randomly: [no/yes, under following basis: ]
- Housing: Individually in wire-bottom cages with a computer-generated unique identification number.
- Diet: Purina Certified Rodent Chow #5002 (Ralston Purina Company, Richmond, IN ad libitum
- Water: Municipal water ad libitum
- Acclimation period: One week
Administration / exposure
- Route of administration:
- oral: gavage
- Vehicle:
- - Vehicle(s)/solvent(s) used: water
- Details on exposure:
- PREPARATION OF DOSING SOLUTIONS:
The test material and CP were dissolved in distilled water. Freshly prepared solutions (less than 2 hours old) were used for dosing the animals. The concentrations of the test material in the dosing solutions used for the micronucleus test were verified by high pressure liquid chromatography (HPLC) by the Analytical Chemistry Laboratory, Health and Environmental Sciences, The Dow Chemical Company, Freeport, Texas (Hinze, 1989).
- All doses of the test material and CP were administered by single oral gavage in aliquots of 10 ml/kgBW. Negative control mice received 10 ml/kgBW water. - Duration of treatment / exposure:
- Single Dose.
- Frequency of treatment:
- Single Dose.
- Post exposure period:
- 24, 48 and 72 hours.
Doses / concentrationsopen allclose all
- Remarks:
- Doses / Concentrations:
0, 500, 1667, 5000mg/kg/BW
Basis:
other: treatment
- Remarks:
- Doses / Concentrations:
0, 50 ,166.7, 500 mg/ml
Basis:
nominal conc.
target concentration
- Remarks:
- Doses / Concentrations:
0, 53.3, 174, 517 mg/ml
Basis:
analytical conc.
- No. of animals per sex per dose:
- 5
- Control animals:
- yes
- Positive control(s):
- cyclophosphamide at a dose level of 120 mg/kgBW.
Examinations
- Tissues and cell types examined:
- Bone marrow polychromatic erythrocytes
- Details of tissue and slide preparation:
- DETAILS OF SLIDE PREPARATION: Cell smears were prepared on microscope slides using small portions of the cell suspension. The slides were allowed to air dry, fixed in methanol and stained in 5% Giemsa.
METHOD OF ANALYSIS:
The slides were coded and scored blindly. One thousand polychromatic erythrocytes were examined from each animal and the number of micronucleated polychromatic erythrocytes (MN-PCE) was recorded. Micronuclei were identified as darkly stained bodies with sharp contours and varying shapes such as round, almond, or ring. The ration of PCE-NCE in the bone marrow was determined by examining 1000 erythyrocytes. The ration was expressed as PCEx100/PCE+NCE. - Evaluation criteria:
- The final interpretation of biological significance of the responses was based on both statistical outcome and scientific judgment.
- Statistics:
- The raw data on the counts of MN-PCE for each animal were first transformed by adding 1 to each count and then taking natural log of the adjusted number. The transformed MN-PCE data and the data on percent PCE were analyzed by a three-way analysis of variance (sex, dose, and time), assuming the three-way interaction to be zero. From this initial analysis, the two-way interactions were reviewed for significance. Depending upon this review, the data were analyzed by either one, two, or three-way analysis of variance looking only at main effects. Pairwise comparisons of treated vs. negative control groups were done, if necessary, by a t-test using Bonferroni correction for multiple comparisons. The alpha level at which all the tests were conducted was 0.01.
The final interpretation of biological significance of the responses was based on both statistical outcome and scientific judgment.
Results and discussion
Test results
- Sex:
- male/female
- Genotoxicity:
- negative
- Toxicity:
- no effects
- Remarks:
- based on lethality
- Positive controls validity:
- valid
- Additional information on results:
- RESULTS OF RANGE-FINDING STUDY
- Clinical signs of toxicity in test animals: All animals survived.
- High dose with and without activation: 5000mg/kg/BW
Any other information on results incl. tables
One female treated with 1667 mg/kgBW TGME died prior to the scheduled time of sacrifice. There were no significant differences in MN-PCE frequencies between the groups treated with the test material and the negative controls. The ratios of PCE to NCE observed in the groups treated with the test material were not significantly different form those of the negative control mice. The body weight data indicated that the animals did not experience any undue stress following treatments.
The positive control chemical, CP, induced a significant increase in the frequencies of micronucleated polychromatic erythryocytes in the bone marrows of both males and females.
Summary of frequencies of micronucleated polychromatic erythrocytes (PCE) in the bone marrow of males.
Concentration (mg/kgbw) |
24 hours |
48 hours |
72 hours |
|||
|
PCE |
% PCE |
PCE |
% PCE |
PCE |
% PCE |
-ve control |
1.0 (1.2) |
71.1 (4.7) |
0.6 (0.9) |
78.7 (6.9) |
0.6 (0.9) |
74.0 (8.7) |
500 |
0.8 (1.3) |
79.1 (7.6) |
0.4 (0.5) |
79.4 (5.9) |
0.8 (0.8) |
76.6 (7.5) |
1667 |
0.2 (0.4) |
68.2 (7.4) |
0.4 (0.9) |
76.8 (11.1) |
0.0 (0.0) |
76.5 (14.6) |
5000 |
0.6 (0.9) |
68.8 (14.5) |
0.2 (0.4) |
79.4 (13.4) |
0.4 (0.5) |
75.3 (8.1) |
+ve control |
62.2 (32.6)* |
67.3(16.4) |
Not tested |
–ve control = water, +ve control = cyclophosphamide (120mg/kg). N=5. Figures in brackets are standard deviations. *=significant (p<0.01) from negative control.
Summary of frequencies of micronucleated polychromatic erythrocytes (PCE) in the bone marrow of females.
Concentration (mg/kgbw) |
24 hours |
48 hours |
72 hours |
|||
|
PCE |
% PCE |
PCE |
% PCE |
PCE |
% PCE |
-ve control |
0.4 (0.9) |
73.5 (6.8) |
1.2 (0.8) |
70.6 (9.8) |
0.4 (0.5) |
76.7 (11.5) |
500 |
0.4 (0.5) |
78.3 (4.8) |
0.6 (0.5) |
80.8 (5.9) |
0.4 (0.9) |
81.2 (4.5) |
1667 |
0.2 (0.4) |
74.8 (2.9) |
0.0 (0.0) |
80.2 (4.9) |
0.6 (0.5) |
82.0 (5.0) |
5000 |
1.6 (0.9) |
69.6 (8.7) |
0.4 (0.5) |
72.1 (6.3) |
1.2 (1.3) |
76.2 (9.8) |
+ve control |
34.6 (9.8)* |
74.0 (8.1) |
Not tested |
–ve control = water, +ve control = cyclophosphamide (120mg/kg). N=5 (except 48hr, 1667 when one animal died prior to scheduled sacrifice time). Figures in brackets are standard deviations. *=significant (p<0.01) from negative control.
Applicant's summary and conclusion
- Conclusions:
- Interpretation of results (migrated information): negative
Based upon the results, it was concluded that the test chemical did not induce a significant increase in the frequencies of micronucleated bone marrow polychromatic erythryocytes when given as single oral dose to male and female CD-1 (ICR) BR mice. Hence, under the experimental conditions used, the test chemical was judged negative in the mouse bone marrow micronucleus test. - Executive summary:
In a guideline (TSCA) and GLP study, TGME did not increase the frequency of micronucleated polychromatic erythrocytes in the bone marrow of mice treated by a single gavage dose up to 5000 mg/kg/day. The percentage of PCEs in bone marrow was also not reduced by TGME treatment.
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.

EU Privacy Disclaimer
This website uses cookies to ensure you get the best experience on our websites.