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EC number: 263-502-0 | CAS number: 62314-22-1
- 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:
- 1997
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- comparable to guideline study
Data source
Reference
- Reference Type:
- publication
- Title:
- Unnamed
- Year:
- 1 998
- Report date:
- 1998
Materials and methods
Test guideline
- Qualifier:
- equivalent or similar to guideline
- Guideline:
- OECD Guideline 408 (Repeated Dose 90-Day Oral Toxicity Study in Rodents)
- Deviations:
- not specified
- GLP compliance:
- not specified
- Limit test:
- no
Test material
- Reference substance name:
- 2-ethylhexanoic acid
- EC Number:
- 205-743-6
- EC Name:
- 2-ethylhexanoic acid
- Cas Number:
- 149-57-5
- Molecular formula:
- C8H16O2
- IUPAC Name:
- 2-ethylhexanoic acid
- Test material form:
- liquid
Constituent 1
- Specific details on test material used for the study:
- 2-Ethylhexanoic acid (EHA; CAS no. 149-57-5) was obtained from Eastman Chemical Company (Kingsport, TN, USA). The purity of the test sample was determined to be 99.920.05%, and the mass spectrum was consistent with the structure of EHA.
Test animals
- Species:
- rat
- Strain:
- Fischer 344
- Details on species / strain selection:
- Male and female weanling F344 rats were obtained from Charles River Laboratories (Wilmington, MA, USA). Females were nulliparous and non-pregnant.
Animals were observed for approximately 2 wk and determined to be healthy prior to testing.All animals were approximately 6 wk of age at the start of
the study. - Sex:
- male/female
- Details on test animals or test system and environmental conditions:
- Husbandry and environmental conditions were in compliance with the NIH Guide to the Use and Care of Animals (86-23). Certified feed (Agway1 ProlabTM Animal Diet RMH 3200) and water were available ad lib
Administration / exposure
- Route of administration:
- oral: feed
- Details on route of administration:
- The test substance was added directly (no vehicle) to chow
- Vehicle:
- unchanged (no vehicle)
- Details on oral exposure:
- Diets were prepared monthly and the concentrations of test diets were verified analytically.
- Analytical verification of doses or concentrations:
- yes
- Details on analytical verification of doses or concentrations:
- Diets were prepared monthly and the concentrations of test diets were verified analytically.
- Duration of treatment / exposure:
- 13 weeks
- Frequency of treatment:
- via Feed ad libitum
Doses / concentrationsopen allclose all
- Dose / conc.:
- 0 other: % w/w
- Dose / conc.:
- 0.1 other: % w/w
- Dose / conc.:
- 0.5 other: % w/w
- Dose / conc.:
- 1.5 other: % w/w
- No. of animals per sex per dose:
- 10 males and 10 females
An additional 10 animals per sex were added to the highdose and control groups to evaluate recovery from any observed toxic efects. - Control animals:
- yes, plain diet
- Positive control:
- No
Examinations
- Observations and examinations performed and frequency:
- Body weight measurements were collected twice during the first week and at least once weekly thereafter, while feed consumption was usually measured twice weekly throughout the study.
Animals were checked daily for mortality.
Observations for clinical signs of toxicity were performed twice each workday, and included examination of the hair, skin, eyes, motor activity, faeces and urine.
Clinical observations for recovery animals were identical to those performed on animals during the test phase of the study. - Sacrifice and pathology:
- All animals were fasted overnight, anaesthetized with CO2, and exsanguinated from the posterior vena cava after collecting blood for analysis.
Complete gross necropsies were performed on all animals. Haematology and serum clinical chemistries were conducted on five animals per sex. - Other examinations:
- Haematology tests included haemoglobin concentration, haematocrit, red blood cell count, white blood cell count, differential white blood cell count, platelet count, red blood cell indices, prothrombin time.
Clinical chemistry tests included: aspartate aminotransferase, alanine aminotransferase (ALT), total bilirubin, total protein, albumin, creatinine, urea nitrogen, glucose, g-glutamyl transpeptidase, triglycerides, cholesterol, sodium, potassium, chloride,
calcium and phosphorous. - Statistics:
- Numerical data were evaluated for statistical significance using the following computer-generated statistical tests: Bartlett’s test (PE0.01), one-way analysis of variance (ANOVA) (PE0.05), and Duncan’s multiple range test (PE0.05).
Results and discussion
Results of examinations
- Clinical signs:
- no effects observed
- Mortality:
- no mortality observed
- Body weight and weight changes:
- no effects observed
- Description (incidence and severity):
- Body weight gain was slightly lower for animals consuming diets containing 1.5% EHA compared with the control groups.
Mean body weights of rats consuming diets containing 0.5% or 0.1% EHA were unaffected compared with controls. - Food consumption and compound intake (if feeding study):
- effects observed, non-treatment-related
- Description (incidence and severity):
- Feed consumption by rats was initially reduced between 19 and 26% in animals consuming the 1.5% diet relative to that of the control group. From day 4 to the end of the treatment period for that group, the average feed consumption was 3–5% lower in males, and 8–10% lower in females when compared with their respective control groups. No dierences in feed consumption were seen for the 0.1 and 0.5% groups or for the 1.5% recovery group compared with controls.
- Food efficiency:
- not specified
- Water consumption and compound intake (if drinking water study):
- not examined
- Ophthalmological findings:
- no effects observed
- Haematological findings:
- effects observed, non-treatment-related
- Description (incidence and severity):
- Minor red blood cell differences (reductions in mean corpuscular haemoglobin and mean corpuscular volume) were observed at the 0.5 and 1.5% dose levels for male and female rats. These dierences were minimal, however, and did not indicate clinically significant changes in red blood cell indices.
- Clinical biochemistry findings:
- effects observed, treatment-related
- Description (incidence and severity):
- Triglyceride concentrations for rats were not significantly different from control values.
The only other change in serum chemistry was an increase in albumin in male rats fed 1.5% EHA; this value returned to control levels after 28 days of recovery. - Urinalysis findings:
- no effects observed
- Behaviour (functional findings):
- not examined
- Immunological findings:
- not examined
- Organ weight findings including organ / body weight ratios:
- effects observed, non-treatment-related
- Description (incidence and severity):
- Mean relative (to body weight) liver weights for all groups of animals receiving 0.5% or 1.5% EHA were greater (PE0.05) than the weights of the respective control groups.
The mean absolute liver weights for all groups fed 1.5% EHA, and for female rats and male mice fed 0.5% EHA were also significantly greater (PE0.05) than for the respective control groups. No other changes in liver weights were noted and following 28 days of recovery, all absolute liver weights were comparable to control values.
Absolute kidney weights were unaffected by EHA treatment.
Minor, yet statistically significant (PE0.05) decreases in absolute brain weights (1.5% female rats) not considered biologically significant.
Slight increases in relative adrenal gland, brain, and testes weights occurred for some of the groups, the differences were related to reduced terminal body weight and, therefore, were not considered to be indicative of organ specific toxicity - Gross pathological findings:
- effects observed, non-treatment-related
- Description (incidence and severity):
- No treatment-related gross pathology was observed for either main-study or recovery animals.
. - Neuropathological findings:
- not examined
- Histopathological findings: non-neoplastic:
- effects observed, non-treatment-related
- Description (incidence and severity):
- Hepatocyte hypertrophy was observed after 13 wk of treatment. No hepatic lesions were observed in rats after recovery.
Hepatomegaly, which was noted in the present study, was interpreted as an adaptive response resulting from enzyme induction, particularly since EHA is known to induce enzyme activity in the liver.
No testicular changes were noted. - Histopathological findings: neoplastic:
- no effects observed
Effect levels
open allclose all
- Key result
- Dose descriptor:
- NOAEL
- Effect level:
- 61 mg/kg bw/day (nominal)
- Based on:
- test mat.
- Sex:
- male
- Basis for effect level:
- organ weights and organ / body weight ratios
- Key result
- Dose descriptor:
- NOAEL
- Effect level:
- 71 mg/kg bw/day (nominal)
- Based on:
- test mat.
- Sex:
- female
- Basis for effect level:
- organ weights and organ / body weight ratios
Target system / organ toxicity
- Key result
- Critical effects observed:
- no
- System:
- other: Liver
- Organ:
- liver
Any other information on results incl. tables
Hepatomegaly, which was noted in the present study, was interpreted as an adaptive response resulting from enzyme induction, particularly since EHA is known to induce enzyme activity in the liver.
Applicant's summary and conclusion
- Conclusions:
- When calculated as a time-weighted average, the three EHA diets provided dose levels of 61, 303 or 917 mg/kg/ day for male rats and 71, 360 or 1068 mg/kg/day for female rats.
The NOAEL for male rats was 61 mg/kg/day and the NOEL for female rats was 71 mg/kg/day.
The lowest-observed-adverse-efect level was approximately 300 mg/kg/day in rats primarily based on potential adverse effects on the liver. Thus, EHA appears to cause similar hepatic effects
to 2-EH following subchronic exposure, but at higher dose levels.
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