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EC number: 202-377-9 | CAS number: 94-96-2
- 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
Toxicity to reproduction
Administrative data
- Endpoint:
- toxicity to reproduction
- Remarks:
- other: Teratology study with information on fertility
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- other: Published in a peer-reviewed journal
Cross-reference
- Reason / purpose for cross-reference:
- reference to same study
Data source
Reference
- Reference Type:
- publication
- Title:
- Unnamed
- Year:
- 1 994
Materials and methods
Test guideline
- Qualifier:
- equivalent or similar to guideline
- Guideline:
- other: OECD 414
- Principles of method if other than guideline:
- GLP teratology study with information on fertility
- GLP compliance:
- yes
- Limit test:
- no
Test material
- Reference substance name:
- 2-ethylhexane-1,3-diol
- EC Number:
- 202-377-9
- EC Name:
- 2-ethylhexane-1,3-diol
- Cas Number:
- 94-96-2
- Molecular formula:
- C8H18O2
- IUPAC Name:
- 2-ethylhexane-1,3-diol
- Test material form:
- liquid: viscous
- Details on test material:
- Purity 99%.
Analysis by NMR and GC/MS
Constituent 1
Test animals
- Species:
- rat
- Strain:
- Sprague-Dawley
- Sex:
- male/female
- Details on test animals or test system and environmental conditions:
- TEST ANIMALS
- Source: Charles River Laboratories, Inc. Portage, MI, USA
- Age at study initiation:
- Weight at study initiation: 250-300 g (males) and 175-200 g (females)
- Housing: two per cage, in stainless steel wire mesh cages
- Diet (e.g. ad libitum): ad libitum
- Water (e.g. ad libitum): ad liitum
- Acclimation period: 2 weeks
ENVIRONMENTAL CONDITIONS
- Temperature (°C): 68-75 F.
- Humidity (%): 42-65
- Photoperiod (hrs dark / hrs light): 12/12
Administration / exposure
- Route of administration:
- dermal
- Vehicle:
- unchanged (no vehicle)
- Details on exposure:
- TEST SITE
- Area of exposure: 1.5 x 1.5 inches
- % coverage:
- Type of wrap if used: occlusive, polyvinyl film over sterilized gauze square. A Lycra-Spandex jacket with Velcro closure covered the dosing site.
- Time intervals for shavings or clipplings: no data, but skin was clipped
REMOVAL OF TEST SUBSTANCE
- Washing (if done): yes, warm water-dampened gauze
- Time after start of exposure: 6 h
TEST MATERIAL
- Amount(s) applied (volume or weight with unit):1.0-4.0 ml/day
- Concentration (if solution): 100%
- Constant volume or concentration used: no
USE OF RESTRAINERS FOR PREVENTING INGESTION: no; applied to dorsal trunk not accessible to mouth - Details on mating procedure:
- - Impregnation procedure: cohoused
- If cohoused:
- M/F ratio per cage: 1/1
- Proof of mating: The presence of a dropped copulation plug was considered evidence of successful mating, and designated as gestation day (gd) 0 - Analytical verification of doses or concentrations:
- no
- Details on analytical verification of doses or concentrations:
- not required for undiluted material
- Duration of treatment / exposure:
- 10 days during gestation
- Frequency of treatment:
- once daily
- Details on study schedule:
- Days 6-15 (inclusive) during gestation
Doses / concentrationsopen allclose all
- Remarks:
- Doses / Concentrations:
4.0 ml/kg bw/d
Basis:
other: undiluted test article based on maternal body weight on GD 6. Equivalent to 3768 mg/kg bw/d.
- Remarks:
- Doses / Concentrations:
2.0 ml/kg bw/d
Basis:
other: undiluted test article based on maternal body weight on GD 6. Equivalent to 1884 mg/kg bw/d.
- Remarks:
- Doses / Concentrations:
1.0 ml/kg bw/d
Basis:
other: undiluted test article based on maternal body weight on GD 6. Equivalent to 942 mg/kg bw/d.
- No. of animals per sex per dose:
- 25 successfully-mated females per dose group
- Control animals:
- yes
- Details on study design:
- Controls were animals where 4.0 ml of water was applied under identical occlusive patches
- Dose selection rationale: Doses were those found to include the NOAEL for repeated dose exposure (see Section 7.5.2, Van Miller, 1994)
- Rationale for animal assignment (if not random): randomly assigned by computer-generated procedure. - Positive control:
- none
Examinations
- Parental animals: Observations and examinations:
- Assessments made on females only.
CAGE SIDE OBSERVATIONS: Yes
- Time schedule: daily, twice daily during the treatment period
DETAILED CLINICAL OBSERVATIONS: Yes
- Time schedule: daily, twice daily during the treatment period for clinical signs of toxicity or pharmacologic effects and local skin irritation
BODY WEIGHT: Yes
- Time schedule for examinations: on days 0, 6, 9, 12, 15, 18 and 21
FOOD CONSUMPTION AND COMPOUND INTAKE (if feeding study): Yes
- Food consumption for each animal determined and mean daily diet consumption calculated as g food/kg body weight/day: Yes, over 3-day intervals from GD 0 to 21.
- Compound intake was calculated as time-weighted averages from the consumption and body weight gain data: No data
POST-MORTEM EXAMINATIONS: Yes
- Sacrifice on gestation day #21 by CO2 asphyxiation
- Organs examined: gravid uterus, ovaries and other pelvic and abdominal visceral were inspected for signs of gross pathology - Oestrous cyclicity (parental animals):
- not examined
- Sperm parameters (parental animals):
- not examined
- Litter observations:
- STANDARDISATION OF LITTERS
- Performed on day 4 postpartum: no, on GD 21.
PARAMETERS EXAMINED
The following parameters were examined in [F1 / F2 / F3] offspring:
[number of corpora lutea, total implants per litter, % preimplantation loss, early and late resorptions, number and sex of pups, sex ratios, stillbirths and dead fetuses, live births, postnatal mortality at GD 21, presence of gross anomalies]
GROSS EXAMINATION OF DEAD PUPS:
[yes, for external and internal abnormalities] - Postmortem examinations (parental animals):
- SACRIFICE
- Male animals: no
- Maternal animals: All survival animals [sacrificed on GD21]
GROSS NECROPSY
- Gross necropsy consisted of [the gravid uterus, ovaries, and other pelvic and abdominal viscera. Ovarian corpora lutea were counted. Maternal and gravid uterine weights were measured. Uteri were dissected longitudinally, and live and dead fetuses and resorption sites counted.
HISTOPATHOLOGY / ORGAN WEIGHTS: yes - Postmortem examinations (offspring):
- GROSS NECROPSY
- Gross necropsy consisted of [external and internal examinations including the cervical and abdominal viscera. One-half of each litter was examined for thoracoabdominal visceral abnormalities. These fetuses were decapitated and the heads fixed in Bouin's fluid for subsequent examination of craniofacial abnormalities using sectioning methods. The remaining fetuses in each litter were eviscerated, fixed in ethanol, processed for staining with alizarin red S, and examined for skeletal malformations and variations.] - Statistics:
- The unit of comparison was the pregnant female or the litter. Quantitative continuous variables were intercompared using Levene's test for equal variances, ANOVA and t-tests with Bonferroni probablilities for pairwise comparisons. When Levene's test indicated heterogeneous variances, all groups were compared by an analysis of variance for unequal variances followed, if necessary, by the separate variance t-test.
Nonparametric data were analyzed statistically by the Kruskal-Wallis test followed by a Mann-Whitney U-test, if appropriate. Incidence data were compared using Fisher's exact test. For all statistical tests, a probability value of p < 0.05 (two-tailed) was used as the criterion for significance.
Results and discussion
Results: P0 (first parental generation)
General toxicity (P0)
- Clinical signs:
- effects observed, treatment-related
- Description (incidence and severity):
- Decreased body weight gain, mild skin irritation and increased liver weights
- Body weight and weight changes:
- effects observed, treatment-related
- Description (incidence and severity):
- Body weights were decreased at the high dose
- Food consumption and compound intake (if feeding study):
- effects observed, treatment-related
- Description (incidence and severity):
- Body weights were decreased at the high dose
- Organ weight findings including organ / body weight ratios:
- effects observed, treatment-related
- Histopathological findings: non-neoplastic:
- not examined
- Other effects:
- no effects observed
Reproductive function / performance (P0)
- Reproductive function: oestrous cycle:
- no effects observed
- Reproductive function: sperm measures:
- not examined
- Reproductive performance:
- not examined
Details on results (P0)
One moribund female of the high dose group was sacrificed on GD11. Necropsy showed hydronephrosis and urinary bladder calculi and therefore death was considered not to be related to treatment. Corrected body weight change was slightly but not statistically significantly reduced at the high dose. Although not significant, maternal body weight gains were lower than for controls for the high dose group over the whole treatment period, particularly during the first 3 days of treatment. There were no significant or dose-related trends for changes in food consumption. There were no treatment-related differences from controls in terminal body weight or gravid uterine weights. Necropsies showed no treatment-related gross pathology in any animal.
There were statistically-significant increases in absolute liver weight at 4.0 ml/kg bw/d, and relative liver weight was increased at all dosages, with mean increases of 15.5% at the high dose, 7.8% at the middle dose, and 7.8% at the low dose.
Effect levels (P0)
- Dose descriptor:
- NOAEL
- Effect level:
- > 3 768 mg/kg bw/day (actual dose received)
- Based on:
- test mat.
- Sex:
- female
- Basis for effect level:
- other: Equivalent to 4.0 ml/kg bw/d
Results: F1 generation
General toxicity (F1)
- Clinical signs:
- not examined
- Mortality / viability:
- no mortality observed
- Body weight and weight changes:
- no effects observed
- Sexual maturation:
- not examined
- Organ weight findings including organ / body weight ratios:
- no effects observed
- Gross pathological findings:
- effects observed, treatment-related
- Description (incidence and severity):
- Increased incidence of visceral malformations and variations
- Histopathological findings:
- no effects observed
Details on results (F1)
There was no statistically significant increase in the incidence of total visceral malformations, but a statistically significant increase in the incidence of unilateral hydroureter, compared with the concurrent controls, was present at the high dose. There was no apparent predominance associated with the side affected. Three visceral variations were statistically significantly increased at high dose: fetal atelectasis or partial fetal atelectasis, bilateral dilated lateral cerebral ventricle, and bilateral dilated ureters. The incidences of dilated lateral ventricle and of bilateral dilated ureter were also significantly increased at the middle dose.
Thirteen skeletal variations indicating reduced ossification were statistically increased for several skeletal districts at the high dose. A reduced number of caudal segments was observed at both the high and low doses.
Overall reproductive toxicity
- Reproductive effects observed:
- not specified
Any other information on results incl. tables
There were no differences in the number of pregnancies resulting from mating as a result of treatment during gestation. There were no differences in reproductive factors or fetal body weights. This included the number of corpora lutea, % preimplantation loss, implantations, implantations per litter, viable implantations, resorptions, % live fetuses per litter, or sex ratio.
Applicant's summary and conclusion
- Conclusions:
- EHD, when applied dermally to the skin of rats, for a duration of 6 h/day during gestation, resulted in minor maternal toxicity but no effects on female reproductive performance or fertility. The NOEL is > 4.0 ml/kg bw/day or 3768 mg/kg bw/day.
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