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EC number: 203-924-4 | CAS number: 111-96-6
- 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
Developmental toxicity / teratogenicity
Administrative data
- Endpoint:
- developmental toxicity
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Study period:
- 3. July 1984 - 18 April 1985
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- comparable to guideline study
Data source
Referenceopen allclose all
- Reference Type:
- study report
- Title:
- Unnamed
- Year:
- 1 987
- Report date:
- 1987
- Reference Type:
- publication
- Title:
- Unnamed
- Year:
- 1 992
- Report date:
- 1992
Materials and methods
Test guideline
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 414 (Prenatal Developmental Toxicity Study)
- Deviations:
- yes
- Remarks:
- no data on food consumption and no. of corpaora lutea
- GLP compliance:
- yes
- Limit test:
- no
Test material
- Reference substance name:
- Bis(2-methoxyethyl) ether
- EC Number:
- 203-924-4
- EC Name:
- Bis(2-methoxyethyl) ether
- Cas Number:
- 111-96-6
- Molecular formula:
- C6H14O3
- IUPAC Name:
- 1-methoxy-2-(2-methoxyethoxy)ethane
- Reference substance name:
- Diethylene glycol dimethyl ether
- IUPAC Name:
- Diethylene glycol dimethyl ether
- Reference substance name:
- Diglyme
- IUPAC Name:
- Diglyme
- Reference substance name:
- Bis(2-methoxyethyl)ether
- IUPAC Name:
- Bis(2-methoxyethyl)ether
- Details on test material:
- Source: Aldrich Chemical Company
Lot: 1617HK
Purity: <99%
Constituent 1
Constituent 2
Constituent 3
Constituent 4
Test animals
- Species:
- rabbit
- Strain:
- New Zealand White
- Details on test animals or test system and environmental conditions:
- TEST ANIMALS
- Source: Dutchland Inc., Denver, PA, USA
- Age at study initiation: approx. 6 months
- Weight at study initiation: 3100-4740 g
- Housing: singly in stainless steel cages with mesh flooring (min. 18"x24"x18" - max. 24"x24"x20)
- Diet (e.g. ad libitum): Purina Certified Rabbit Chow (5322), ad libitum
- Water (e.g. ad libitum): deionized/filtered water, ad libitum
- Acclimation period: 14 days
ENVIRONMENTAL CONDITIONS
- Humidity: 53%
- Temperature: 68°F
- Air changes (per hr): 12 - 14 times per hour
- Photoperiod (hrs dark / hrs light): 12/12
Administration / exposure
- Route of administration:
- oral: gavage
- Vehicle:
- water
- Details on exposure:
- Artificially inseminated, timed-pregnant New Zealand White rabbits were dosed daily with Diglyme or vehicle on gestation day (gd) 6 though 19. Treatment wass administered by gavage. A dose volume of 3.0 mL/kg bw was used. The volume administered to each animal was adjusted according to daily body weight taken just prior to dosing on gd 6 through 19.
A. First preliminary study: Diglyme was administered at dose levels of 0, 100, 200, and 400 mg/kg bw/d (4 animals/dose level)
B. Second preliminary study: Diglyme was administered at dose levels of 0, 25, 50, 100, and 150 mg/kg bw/d (6 animals/dose level)
C. Main study dose levels: 0, 25, 50, 100, and 175 mg/kg bw/d at 15-25 animals/dose level) - Analytical verification of doses or concentrations:
- yes
- Details on analytical verification of doses or concentrations:
- Gas chromatography
- Details on mating procedure:
- atrificially inseminated
- Duration of treatment / exposure:
- gd 6 through 19 (14 days)
- Frequency of treatment:
- daily
- Duration of test:
- duration of treatment: 14 days
termination: gd 30
Doses / concentrationsopen allclose all
- Dose / conc.:
- 0 mg/kg bw/day
- Dose / conc.:
- 25 mg/kg bw/day
- Dose / conc.:
- 50 mg/kg bw/day
- Dose / conc.:
- 100 mg/kg bw/day
- Dose / conc.:
- 175 mg/kg bw/day
- No. of animals per sex per dose:
- 25 - 32
- Control animals:
- yes, concurrent vehicle
- Details on study design:
- On the basis of the observation of complete resorptions at dose levels of 200 mg/kg bw/d and above, an apparent increase in prenatal deaths at 25 mg/kg bw/d and above, maternal toxicity (weight loss) at 25 mg/kg bw/d, and icreased mortality of the dams at 100 mg/kg bw/d and above the dose levels for the main study were fixed.
Examinations
- Maternal examinations:
- Rabbits were weighed on gd 0 as well as daily on days 6 - 19 and prior to euthanasia on gd 30. Dams were observed daily during treatment for clinical signs of toxicity.
- Ovaries and uterine content:
- Following euthanasia, maternal liver weight and gravid uterine weight were measured. Uterine contents were evaluated for the number of implantation sites, resorptions, late fetal deaths (fetuses heavier than 10 g but displaying no vital signs) and live fetuses. the uterus was stained to reveal possible early resorptions when visible evidence of pregnancy was not apparent.
- Fetal examinations:
- Live fetuses were weighed and examined for exrernal abnormalities followed by evaluation for visceral malformations using a fresh tissue dissection technique. Half of the fetuses were decapitated after dissection and the heads were fixed in Bouin's solution for free-hand sectioning and axmaination. All fetal carcasses were cleared and stained with Alcian blue/Alizarin red S and examined for skeletal alterations.
- Statistics:
- Analyses were carried out using the general linear model procedure in the SAS software library (SAS Institute, Inc. 1985). Prior to analysis, an arcsine-square root transformation was performed on all litter-derived percentage data. Dose-response relationships for selected measures were evaluated using a test for linear trend. Analysis if variance (ANOVA) tests were used to determine whether significant dose effects, replicate effects, or dose x replicate interactions had occured. When ANOVA revealed significant differences among groups, then William's multiples comparison test and Dunnett's test were used to compare treated groups to the vehicle control group. Nominal scale measures analyzed by a test for linear trend on proportions and a chi square test for independence among treatment groups. When chi square revealed significant (p<0.05) differences among groups, then a one-tailed Fisher's exact probability test was used for pairwise comparisons between each Diglyme treated group and the vehicle control group.
- Indices:
- no data
- Historical control data:
- no data
Results and discussion
Results: maternal animals
General toxicity (maternal animals)
- Clinical signs:
- effects observed, treatment-related
- Description (incidence and severity):
- Clinical signs were limited to a decreased fecal output at the high dose level.
- Dermal irritation (if dermal study):
- not examined
- Mortality:
- mortality observed, treatment-related
- Description (incidence):
- There was an increase in treatment-related maternal mortality at the highest dose level ( 15 vs. 4% in controls).
- Body weight and weight changes:
- effects observed, treatment-related
- Description (incidence and severity):
- There was a loss of weight during the days of chemical treatment at dose levels of 50 mg/kg bw/d and above, with the difference from control statistically significant at each of these dose levels.
- Food consumption and compound intake (if feeding study):
- not examined
- Food efficiency:
- not examined
- Water consumption and compound intake (if drinking water study):
- not examined
- Ophthalmological findings:
- not specified
- Haematological findings:
- not examined
- Clinical biochemistry findings:
- not examined
- Endocrine findings:
- not examined
- Urinalysis findings:
- not examined
- Behaviour (functional findings):
- not examined
- Immunological findings:
- not examined
- Organ weight findings including organ / body weight ratios:
- effects observed, treatment-related
- Description (incidence and severity):
- A decrease in weight of the gravid uterus was observed that was statistically significant at the two highest dose levels (100 and 175 mg/kg bw/d). The body weight gain, corrected for gravid uterine weight, did not differ from that of the control group in any of the dose groups.
- Gross pathological findings:
- not examined
- Neuropathological findings:
- not examined
- Histopathological findings: non-neoplastic:
- not examined
- Histopathological findings: neoplastic:
- not examined
- Other effects:
- effects observed, treatment-related
- Description (incidence and severity):
- From 75 to 100% of the bred females in the various groups were pregnant.
Maternal developmental toxicity
- Number of abortions:
- not examined
- Pre- and post-implantation loss:
- no effects observed
- Total litter losses by resorption:
- effects observed, treatment-related
- Description (incidence and severity):
- Significant increase in prenatal mortality at the two highest dose levels (100 and 175 mg/kg bw/d). This loss was due largely to the total resorption of 2 of 21 litters at 100 mg/kg bw/d and 5 of 17 litters at 175 mg/kg bw/d.
- Early or late resorptions:
- not specified
- Dead fetuses:
- effects observed, treatment-related
- Description (incidence and severity):
- There was a significant increase in prenatal mortality at the two highest dose levels (100 and 175 mg/kg bw/d). This loss was due largely to the total resorption of 2 of 21 litters at 100 mg/kg bw/d and 5 of 17 litters at 175 mg/kg bw/d.
- Changes in pregnancy duration:
- not examined
- Changes in number of pregnant:
- not examined
Effect levels (maternal animals)
- Dose descriptor:
- NOAEL
- Effect level:
- 50 mg/kg bw/day
- Basis for effect level:
- other: maternal toxicity
Results (fetuses)
- Fetal body weight changes:
- effects observed, treatment-related
- Description (incidence and severity):
- There was a significant decreasing trend in fetal body weight but no group mean was significantly different from that of the controls. There was no evidence of a sex difference in either of these parameters - live fetuses/litter of fetal body weight.
- Reduction in number of live offspring:
- not examined
- Changes in sex ratio:
- no effects observed
- Changes in litter size and weights:
- no effects observed
- Anogenital distance of all rodent fetuses:
- not examined
- Changes in postnatal survival:
- not examined
- External malformations:
- not specified
- Skeletal malformations:
- effects observed, treatment-related
- Description (incidence and severity):
- Significantly increased malformations at 100 and 175 mg/kg bw/d.
Most prevalent malformations were fused ribs in 17% (13/77) in high dose fetuses. - Visceral malformations:
- effects observed, treatment-related
- Description (incidence and severity):
- Significantly increased malformations at 100 and 175 mg/kg bw/d. Most prevalent malformations were hydronephosis in 23% (18/77) of high-dose fetuses.
- Other effects:
- effects observed, treatment-related
- Description (incidence and severity):
- The percentage of adversely affected (includes resorptions, late fetal death and malformed fetuses) implants/litter was significantly increased above control at dose levels of 50 mg/kg bw/d and above.
In contrast, female pups tended to have more malformations than males, with percentage of malformed fetuses per litter being significantly increased at both 100 and 175 mg/kg bw/d among female pups and only at the highest dose level among males.
Effect levels (fetuses)
- Key result
- Dose descriptor:
- NOAEL
- Effect level:
- 25 mg/kg bw/day
- Basis for effect level:
- other: adverse effects on prenatal growth, viability and morphological development
Fetal abnormalities
- Abnormalities:
- effects observed, treatment-related
- Localisation:
- skeletal: rib
- other: hydronephosis, clubbing of the fore- and hindlimbs
Overall developmental toxicity
- Developmental effects observed:
- yes
- Lowest effective dose / conc.:
- 25 mg/kg bw/day
- Treatment related:
- yes
- Relation to maternal toxicity:
- developmental effects in the absence of maternal toxicity effects
Applicant's summary and conclusion
- Conclusions:
- Exposure of New Zealand white rabbits to Diethylene glycol dimethyl ether at 25 mg/kg bw/d during gd 6 through 19 produced no adverse developmental effects. Doses of 50 mg/kg bw/d and above were associated with resorptions, late fetal death and malformed fetuses. The NOAEL (maternal) is considered to be 50 mg/kg bw/d.
- Executive summary:
Diethylene glycol dimethyl ether (0, 25, 50, 100, or 175 mg/kg bw/d) were administered by gavage in distilled water to timed-pregnant New Zealand white rabbits (15 -25 dams/group) during gd 6 -19. Treated females were euthanized on gd 30, uterine contents were examined, and live fetuses were examined for morphological alterations. Evidence of maternal toxicity, per se, was observed only at 175 mg/kg bw/d with 15% mortality among treated females compared to 4% among controls. No significant maternal toxicity was observed in the 25 mg/kg bw/d group, and only minimal maternal toxicity (decreased maternal weight gain during treatment) was observed at 50 and 100 mg/kg bw/d compared to vehicle group.The NOAEL (developmental) was 25 mg/kg bw/d, the NOAEL (maternal) 50 mg/kg bw/d. The incidences of prenatal mortality and malformed live fetuses were significantly above controls at 100 and 175 mg/kg bw/d. Malformations observed most frequently included fusion of ribs to each other and hydronephrosis; clubbing of the limbs without underlying bone deformities, a variation, was also observed.
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