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EC number: 203-874-3 | CAS number: 111-48-8
- 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:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- other: Guideline study with acceptable restrictions. Restrictions: no details about the purity of the TS.
Data source
Referenceopen allclose all
- Reference Type:
- study report
- Title:
- Unnamed
- Year:
- 2 001
- Reference Type:
- publication
- Title:
- Toxicity Assessment of Thiodiglycol
- Author:
- Reddy G, Major MA, Leach GJ
- Year:
- 2 005
- Bibliographic source:
- International Journal of Toxicology, 24:435–442
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:
- adopted 1997
- GLP compliance:
- yes
- Type of assay:
- micronucleus assay
Test material
- Reference substance name:
- Reference substance 001
- Details on test material:
- Lot No. 05701EQ, further data available from the sponsor
Constituent 1
Test animals
- Species:
- mouse
- Strain:
- ICR
- Sex:
- male
- Details on test animals or test system and environmental conditions:
- - Strain: Crl:CD-1(ICR) BR
- obtained from Charles River Lab, Raleigh (North Carolina) (preliminary study) or St. Constant (Quebec) (main study)
- at least 6 days acclimatization period
- randomization of animals
- at start of treatment period in the main study males ca. 8 weeks old, bw range 30.0-34.5 g; in the preliminary study males and females ca. 8 weeks old, bw range
30.2-34.8 g and 22.8-25.4 g, respectively
HOUSING and DIET
- animals housed in dose groups; polycarbonate cages used with hardwood chip laboratory bedding.
- temperature 18-26°C; 30-70% relative humidity; light/dark cycle 12h/12h; ventilation at least 10 air changes per h;
- certified rodent diet #5002 and tap water ad libitum; no contaminants in diet, water and wood chips (analysed)
Administration / exposure
- Route of administration:
- oral: gavage
- Vehicle:
- sterile deionized water
- Details on exposure:
- - Formulation procedure (main study)
Test substance (TS) dissolved in the vehicle (sterile deionized water) immediatly before use; concentrations of 0, 50, 100, 200 mg/ml TS or 8 mg/ml cyclophosphamide (positive control); administration volume 10 ml/kg bw in all groups. - Duration of treatment / exposure:
- Single exposure
- Frequency of treatment:
- Once
- Post exposure period:
- 24 and 48 h
Doses / concentrations
- Remarks:
- Doses / Concentrations:
0, 500, 1000, 2000 mg/kg bw
Basis:
actual ingested
- No. of animals per sex per dose:
- 6 males in the main study
- Control animals:
- yes, concurrent vehicle
- Positive control(s):
- gavaged once with 80 mg/kg bw cyclophosphamide
Examinations
- Tissues and cell types examined:
- Bone marrow smears prepared (air dried, fixed with methanol)
- Details of tissue and slide preparation:
- Slides stained with May-Grünwald followed by Giemsa staining) for microscopic examination. Evaluation of slides on a blind basis; for each mouse, the number of micronucleated polychromatic erythrocytes (MPE) counted in 2000 polychromatic erythrocytes (PE); the ratio of PE versus normochromatic erythrocytes (NE) determined by scoring 500 erythrocytes per mouse; historical background frequency of micronuclei in this strain at this lab is 0.0 to 0.4%.
- Evaluation criteria:
- A statistical significant increase in the frequency of MPE must be demonstrated for at least one dose level, and a statistically significant dose-related response; historical data and other considerations of biological relevance were taken into account.
- Statistics:
- Data analysed by using an analysis of variance (Winer, 1971) on untransformed proportions of cells with micronuclei per mouse and on untransformed PE:NE ratios when the variances were homogeneous; ranked proportions used for heterogeneous variances; differences from control analysed by Dunnett's t-test; parametric and nonparametric tests used for trend analysis.
Results and discussion
Test results
- Sex:
- male
- Genotoxicity:
- negative
- Toxicity:
- no effects
- Vehicle controls validity:
- valid
- Positive controls validity:
- valid
- Additional information on results:
- - Preliminary toxicity test
no clinical signs at any dose level; 2000 mg/kg bw used for the main study
- Clinical signs in the main study
no clinical signs observed in any group
- Cytogenetic in the main study
no significant differences in MPE values between vehicle controls and TS treated males of all dose groups; the PN/NE ratio was also not significantly altered in any TS treatment group; valid positive and negative control (also in comparison with historical data)
Any other information on results incl. tables
Cytogenetic summary table
Dose in mg/kg bw % MPE (SE) PE/NE ratio (SE)
and harvest time
vehicle 24 h 0.13 (0.02) 0.91 (0.03)
vehicle 48 h 0.09 (0.01) 0.84 (0.06)
500 24 h 0.09 (0.03) 0.79 (0.03)
1000 24 h 0.12 (0.03) 0.79 (0.04)
2000 24 h 0.11 (0.02) 0.82 (0.05)
2000 48 h 0.10 (0.02) 0.91 (0.04)
positive
control 24 h 3.07 (0.35)** 0.67 (0.04)*
SE: standard error; *: p<0.05; **: p<0.01
Applicant's summary and conclusion
- Conclusions:
- Interpretation of results (migrated information): negative
No mutagenic activity in the mouse bone marrow micronucleus test at dose levels up to 2000 mg/kg bw. - Executive summary:
Guideline study with acceptable restrictions (no details about the test substance).
In the mouse bone marrow micronucleus assay 6 male mice per dose were gavagaed once with 0, 500, 1000, or 2000 mg/kg and bone marrow prepared for evaluation 24 and 48 h after application. No increase in the frequency of micronuclei was detected. No clinical toxicity or cytotoxic effects on the bone marrow were found even at 2000 mg/kg bw, the highest test dose recommended by the current guideline. The positive controls were valid.
Conclusion: No mutagenic activity in the mouse bone marrow micronucleus test at dose levels up to 2000 mg/kg bw.
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