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EC number: 203-713-7 | CAS number: 109-86-4
- 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

Repeated dose toxicity: oral
Administrative data
- Endpoint:
- sub-chronic toxicity: oral
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Study period:
- 1993
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- other: A fully peer reviewed GLP study carried out by a reputable organisation to recognised scientific principles.
Data source
Reference
- Reference Type:
- publication
- Title:
- Unnamed
- Year:
- 1 993
- Report date:
- 1993
Materials and methods
- Principles of method if other than guideline:
- Toxicology study carried out following a range finder study to determine appropriate doses. Exposure by drinking water with normal end points used for such a repeat dose study, including histopathology, haematology, clinical chemistry, urinalysis and reproductive system parameters.
- GLP compliance:
- yes
- Remarks:
- USA regulations 21 CFR 58
- Limit test:
- no
Test material
- Reference substance name:
- 2-methoxyethanol
- EC Number:
- 203-713-7
- EC Name:
- 2-methoxyethanol
- Cas Number:
- 109-86-4
- Molecular formula:
- C3H8O2
- IUPAC Name:
- 2-methoxyethanol
- Details on test material:
- - Methoxyethanol purity: 98%
- Analytical purity: checked
- Supplied by Kodak laboratories
Constituent 1
Test animals
- Species:
- rat
- Strain:
- Fischer 344
- Sex:
- male/female
- Details on test animals or test system and environmental conditions:
- TEST ANIMALS
- Age at study initiation: 6 weeks
- Housing: 5 per cage
- Diet: ad libitum
- Water: ad libitum
- Acclimation period: 11 - 12 days
ENVIRONMENTAL CONDITIONS
- Temperature: 60-77F
- Humidity: 20-70% RH respectively
- Photoperiod: fluorescent tube, 12hrs/day.
Administration / exposure
- Route of administration:
- oral: drinking water
- Analytical verification of doses or concentrations:
- yes
- Details on analytical verification of doses or concentrations:
- Preliminary studies confirmed stability of stock solutions for 3 weeks under appropriate storage conditions and for 4 days in rodent drinking water bottles.
- Duration of treatment / exposure:
- 90 days
- Frequency of treatment:
- continous
Doses / concentrationsopen allclose all
- Remarks:
- Doses / Concentrations:
0, 750, 1500, 3000, 4500 or 6000 ppm
Basis:
nominal in water
- Remarks:
- Doses / Concentrations:
70, 135, 297, 546, 785 mg/kg
Basis:
other: actual ingested - females
- Remarks:
- Doses / Concentrations:
71, 165, 324, 715, 806 mg/kg
Basis:
other: actual ingested - males
- No. of animals per sex per dose:
- 10m/10f
- Control animals:
- yes, concurrent no treatment
- Details on study design:
- - Dose selection rationale: range finder study
Examinations
- Observations and examinations performed and frequency:
- CAGE-SIDE OBERVATIONS: Yes
- All rats were observed twice daily throughout the study.
DETAILED CLINICAL OBSERVATIONS: Yes
- Time schedule: at the beginning of the study and then weekly until the end of the study.
BODY WEIGHT: Yes
- Time schedule for examinations: recorded at the beginning of the study and then weekly until the end of the study.
FOOD CONSUMPTION AND COMPOUND INTAKE (if feeding study):
- Estimates of compound consumption based on water consumption by rats as shown above in doses/concentration section. Measured by cage twice per week.
HAEMATOLOGY: Yes, Series 7000 cell counter and a Series 810 whole blood platelet analyzer (Baker Instruments). Supplemental groups of 10 rats/sex/group/time point were included for haematology and clinical chemistry observations at weeks 1 and 3. Parameters checked: HgB, HCT, RBC count, MCV, MCH, MCHC, platelets, reticulocytes, WBC total and differential count, nucleated erythrocytes, methemoglobin concentrations, bone marrow cellularity.
CLINICAL CHEMISTRY: Yes, measured with a Cobra Fara analyser (Roche Diagnostics). Parameters examined: urea nitrogen, creatinine, total protein, albumin, ALP, ALT, creatine kinase, bile acids.
URINALYSIS: Yes
- Time schedule for collection of urine: last 24 hours prior to sacrifice
- Metabolism cages used for collection of urine: Yes
- Animals fasted: No, but no water during collection period.
- Parameters checked: volume, gravity, pH
OTHER: Evaluations of vaginal cytology and sperm morphology were done for the three highest doses tested. Results concerning these examinations are reported in more detail in the reprotoxicity section. - Sacrifice and pathology:
- GROSS PATHOLOGY: Sacrifice: 70% CO2:30% O2 asphyxiation. Yes, complete autopsies were made on all study rats. Organs examined in control and high dose groups: adrenals, bone (femur) with marrow, brain (3 transverse sections), esophagus, eyes, heart/aorta, intestines, (cecum, duodenum, jejunum, ileum, colon, rectum), kidneys, larynx, liver, lung, lymph node (mesenteric, mandibular), mammary gland, nasal cavity and turbinates, ovaries, pancreas, parathyroids, pituitary, pharynx, preputial or clitoral glands, prostate, salivary gland, seminal vesicles, skin, spinal cord, spleen, stomach (fore and glandular), testes, thigh muscle, thyroid, tongue, trachea, urinary bladder, uterus, vagina, all gross lesions. In low dose group: bone marrow, epididymis, liver, spleen, testis and uterus. Organs weighed: heart, liver, kidney, lung, thymus and testes were examined.
HISTOLOGY: Tissues to be examined fixed, embedded, sectioned and stained (H&E) for microscopic examination. Tissues were examined from all control group and treated rats. Bone marrow cells collecetd from right femur for total nucleated cell counts.
OTHER: A stop-exposure group of 30 male rats was also included. 30 males were dosed at 0, 1500, 3000 and 6000ppm for 60 days. Groups of 10 were sacrificed at this time point and then 30 and 56 days after recovery. - Other examinations:
- In addition, a stop exposure study group was included. 30 male rats administered 2 -methoxyethanol at given doses for 60 days. Half animals necropsied. If lesions were seen, remaining animals were kept for 56 day recovery period
- Statistics:
- Parametric multiple comparison methods: Organ and body weight
Non-parametric multiple comparison methods: clinical chemistry/haematology data
Jonckheere's test: for trend/dose response.
Results and discussion
Results of examinations
- Clinical signs:
- effects observed, treatment-related
- Mortality:
- mortality observed, treatment-related
- Body weight and weight changes:
- effects observed, treatment-related
- Water consumption and compound intake (if drinking water study):
- effects observed, treatment-related
- Ophthalmological findings:
- not examined
- Haematological findings:
- effects observed, treatment-related
- Clinical biochemistry findings:
- effects observed, treatment-related
- Urinalysis findings:
- effects observed, treatment-related
- Behaviour (functional findings):
- not examined
- Organ weight findings including organ / body weight ratios:
- effects observed, treatment-related
- Gross pathological findings:
- effects observed, treatment-related
- Histopathological findings: non-neoplastic:
- effects observed, treatment-related
- Histopathological findings: neoplastic:
- not examined
- Details on results:
- CLINICAL SIGNS AND MORTALITY
Chemical related mortality was seen reaching 100% at the highest dose. In group with 100% survival there was a decrease in water consumption for males (3000ppm) and females (1500ppm) and a significant dose related body weight decrease evident for both sexes from 1500ppm. Clinical signs of toxicity included tremors, diarrhea, emaciation, abnormal posture, pallor, tachypenia, hypoactivity and a comatose state. Both sexes showed a normochromic, normocytic, poorly regenerative (decreased reticulocyte count) anaemia and leucopenia which persisted at all time points. Bone marrow cellularity was also reduced but recovered during the study and was only evident at in the higher dose males (4500ppm) at the end of the study.
BODY WEIGHT and WATER CONSUMPTION
Reduced body weight was seen in the 1500ppm dose groups upwards as was water consumption.
HAEMATOLOGY
Normocytic anaemia (poorly regenerative), leukopenia (reduced neutrophil and lymphocyte count) and thrombocytopenia were observed associated with decreases in haemocrit and haemoglobin concentrations and reduced RBC, platelet and leucocyte count. Bone marrow cellularity reduced in higher dose groups.
CLINICAL CHEMISTRY
Changes in clinical chemistry were consistent with decreased food intake.
URINALYSIS
Decreased volume and increased specific gravity, consistent with reduced drinking water intake.
ORGAN WEIGHTS
Changes in all organ weights, except thymus and testes, were consistent with reduced body weight. For the thymus, epididymus and testes, dose related weight decreases were seen (both sexes for thymus and down to the lowest dose level.) Almost all other gross lesions were related to reduced body weight.
HISTOPATHOLOGY: NON-NEOPLASTIC
Histopathological changes to the testes consisted of minimal to marked degeneration of the germinal epithelium of the seminferous tubules(STs). In more severe cases atrophic STs contained only Sertoli cells and a few spermatogonia. Reduced sperm number and cell debris were also seen in the epididymus lumen. Degeneration was also seen at a minimal level in 7/10 rats at 750ppm. Chemical related fibrosis (focal thickening) of the splenic capsule was also seen in both sexes at 1500ppm and above. Other histopathological changes were thought to be secondary to general toxicity as demonstrated by marked body weight loss.
OTHER FINDINGS
Sperm motility and defects were drastically effected from 1500ppm upwards with a slight but significant reduction in concentration seen at 750ppm. In females, there was no significant changeswere no significant changes in estrous cycle length but some evidence to suggest time in estrous was reduced. In the stop exposure study, all animals at 6000ppm died. The recovery animals still showed a body weight reduction of at least 9% compared to controls even after 56 days. Histopathological examination of the testes showed some recovery from the degenerative lesions but damage remained permanent.
Effect levels
open allclose all
- Dose descriptor:
- LOAEL
- Effect level:
- 71 other: mg/kg/bw
- Sex:
- male
- Basis for effect level:
- other: histopathology (testes), organ weights (thymus)
- Dose descriptor:
- NOAEL
- Effect level:
- < 71 other: mg/kg/bw
- Sex:
- male
- Basis for effect level:
- other: histopathology (testes), organ weights (thymus)
Target system / organ toxicity
- Critical effects observed:
- not specified
Applicant's summary and conclusion
- Conclusions:
- No NOAEL established since testicular degeneration in males and decreased thymus weights in males and females occurred at the lowest concentration administered.
- Executive summary:
In a well conducted drinking water study, rats were exposed to methoxyethanol at concentrations ranging from 750 -6000ppm for a period of 90 days. A NOAEL was not established in the study as the lowest dose tested, equivalent to 70 -71mg/kg produced adverse changes to the male testes (degeneration). At this dose, both sexes also showed a significant reduction in thymus weight, both relative and absolute. Bone marrow cellular depletion, splenic atrophy and/or capsular fibrosis and thymic atrophy were apparent in both sexes from doses of 135 -165mg/kg upwards.
Synopsis
NOAEL (91day), rat, male/female <71mg/kg/day
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