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EC number: 203-631-1 | CAS number: 108-94-1
- 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: inhalation
Administrative data
- Endpoint:
- sub-chronic toxicity: inhalation
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- comparable to guideline study
Data source
Reference
- Reference Type:
- publication
- Title:
- Unnamed
- Year:
- 2 018
- Report date:
- 2018
Materials and methods
Test guideline
- Qualifier:
- equivalent or similar to guideline
- Guideline:
- OECD Guideline 413 (Subchronic Inhalation Toxicity: 90-Day Study)
- Deviations:
- not specified
- Remarks:
- no historical control data; whole body exposure without justification
- GLP compliance:
- yes
- Limit test:
- no
Test material
- Reference substance name:
- Cyclohexanone
- EC Number:
- 203-631-1
- EC Name:
- Cyclohexanone
- Cas Number:
- 108-94-1
- Molecular formula:
- C6H10O
- IUPAC Name:
- cyclohexanone
Constituent 1
- Specific details on test material used for the study:
- SOURCE OF TEST MATERIAL
- Source: ACROS, Netherlands
- Lot no.: SNGYB and B2XGG
- Purity: 99.7% (SNGYB) and 99.6% (B2XGG)
Test animals
- Species:
- other: mouse and rat
- Strain:
- other: B6C3F1 and F344
- Details on species / strain selection:
- Species were selected for the study because these animals are generally used in subchronic toxicity studies and the availability of considerable
background information for these species. - Sex:
- male/female
- Details on test animals or test system and environmental conditions:
- TEST ANIMALS
- Source: Japan SLC, Inc. (Shizuoka, Japan)
- Age at study initiation: 6 weeks
- Housing: single
- Diet: provided rodent diet
- Water: filtered tap water
- Acclimation period: 1 week
DETAILS OF FOOD AND WATER QUALITY:
ENVIRONMENTAL CONDITIONS
- Temperature (°C): 22 +/- 3
- Humidity (%): 50 +/- 20
- Air changes (per hr): 10-20
- Photoperiod (hrs dark / hrs light): not specified
Administration / exposure
- Route of administration:
- inhalation: vapour
- Type of inhalation exposure:
- whole body
- Vehicle:
- clean air
- Details on inhalation exposure:
- GENERATION OF TEST ATMOSPHERE / CHAMBER DESCRIPTION
- Exposure apparatus: LVG-04-A, HCT Co., Seoul, Korea
- Method of concentration analysis: valve control system (VCS-06, HCTm, Seoul, Korea) and GC (Trace 1300, Thermo Fischer Scientific Co., Waltham, MA)
- System of generating particulates/aerosols: saturated vapor was evaporated by bubbling clean air and using a hot water bath.
TEST ATMOSPHERE
- Samples taken from breathing zone: yes - Analytical verification of doses or concentrations:
- yes
- Details on analytical verification of doses or concentrations:
- Cyclohexanone concentrations in the chambers were automatically recorded through the valve control system (VCS-06, HCTm, Seoul, Korea) by using a pump and analyzed by gas chromatography (Trace 1300, Thermo Fisher Scientific Co., Waltham, MA) at 30-min intervals during the exposure period.
- Duration of treatment / exposure:
- 13 weeks
- Frequency of treatment:
- 6 h/day, 5 days/week
Doses / concentrationsopen allclose all
- Dose / conc.:
- 100 ppm
- Remarks:
- equivalent to ca. 408 mg/m³
- Dose / conc.:
- 250 ppm
- Remarks:
- equivalent to ca. 1020 mg/m³
- Dose / conc.:
- 625 ppm
- Remarks:
- equivalent to ca. 2550 mg/m³
- No. of animals per sex per dose:
- 10
- Control animals:
- yes, concurrent vehicle
- Details on study design:
- - Dose selection rationale:
The highest exposure concentration of 650 ppm was selected based on the results of an acute inhalation toxicity study (Smyth et al., 1969;mOECD, 1996) which reported 1/6 rats exposed to 2000 ppm for 4 h died and a 4-week repeated inhalation toxicity study (Lee et al., 2018) which reported no effects at exposure concentrations up to 250 ppm in B6C6F1 mice. In addition, conditions of generation of cyclohexanone before starting the study were checked, and it was confirmed that the highest concentration that can be stably and continuously generated at the facility was 650 ppm. - Positive control:
- no positive control included
Examinations
- Observations and examinations performed and frequency:
- CAGE SIDE OBSERVATIONS: Yes
- Time schedule: Daily
DETAILED CLINICAL OBSERVATIONS: Yes / No / Not specified
- Time schedule:
BODY WEIGHT: Yes
- Time schedule for examinations: weekly
FOOD CONSUMPTION AND COMPOUND INTAKE: Yes
- Time schedule for examinations: weekly
FOOD EFFICIENCY:
- Body weight gain in kg/food consumption in kg per unit time X 100 calculated as time-weighted averages from the consumption and body weight gain data: Yes / No / Not specified
WATER CONSUMPTION AND COMPOUND INTAKE (if drinking water study): No
OPHTHALMOSCOPIC EXAMINATION: Yes
- Time schedule for examinations: start of treatment and in the last week of exposure period
- Dose groups that were examined: all animals (start) and control and high dose (last week)
HAEMATOLOGY: Yes
- Time schedule for collection of blood: At necropsy
- Anaesthetic used for blood collection: Yes (isoflurane)
- Animals fasted: No
- How many animals: All surviving animals
- Checked parameters: leucocyte, platelet (PLT) count,
erythrocyte count, hemoglobin, hematocrit, mean corpuscular
volume, mean corpuscular hemoglobin, mean corpuscular
hemoglobin (MCH) concentration, prothrombin time
(PT, mice only), and activated partial thromboplastin time
(mice only).
CLINICAL CHEMISTRY: Yes
- Time schedule for collection of blood: At necropsy
- Parameters checked: glucose, total
bilirubin, blood urea nitrogen (BUN), potassium, total protein,
calcium, albumin (ALB), chloride, creatinine, inorganic
phosphorus, total cholesterol (TCHO), sodium, triglyceride,
aspartate aminotransferase (AST), alanine aminotransferase
(ALT), alkaline phosphatase (ALP), and c-glutamyl transpeptidase
URINALYSIS: No
NEUROBEHAVIOURAL EXAMINATION: No
IMMUNOLOGY: No - Sacrifice and pathology:
- GROSS PATHOLOGY: Yes.
- Organs that were weighed: adrenal glands, ovaries (female only), brain, spleen, epididymides (male only), testes (male only), heart, thymus, kidneys, uterus (female only), liver, and lung
HISTOPATHOLOGY: Yes
- Organs checked: ovaries (female only), adrenal glands, pancreas, parathyroid glands, aorta (thoracic), pituitary gland, brain, prostate (male only), bone marrow, rectum, cecum, salivary glands, colon, sciatic nerve, duodenum, seminal vesicle (male only), epididymides (male only), skeletal muscle, esophagus, skin, eyes (with optic nerve), spinal cord (cervical, thoracic, lumbar), femur (F-T joint), spleen, gall bladder (mice only), Harderian glands, sternum, heart, stomach, ileum, teeth, jejunum, testes (male only), kidneys, thymus, larynx, thyroids, liver, trachea, lung, urinary bladder, lymph node, uterus with cervix (female only), mammary gland (female only), vagina (female only), and nasopharyngeal tissue.
- In addition to histopathological examination of the high exposure group of animals,
histopathological examination of the skin (mice only), liver (rats only) and kidney (rats only) was performed for all animals of the low- and medium-concentration groups. - Statistics:
- Homogeneity of the variances: Levene test
When variances were homogeneous: one-way ANOVA
Differences between control and treated groups: Dunnett's test
Heterogeneity of the variances: Kruskal-Wallis test
Differences between control and treated groups: Dunn's rank sum test
Results and discussion
Results of examinations
- Clinical signs:
- no effects observed
- Description (incidence and severity):
- RATS
no effects observed
MICE
In all test groups, loss of hair was noted - Mortality:
- mortality observed, non-treatment-related
- Description (incidence):
- RATS
no mortality observed
MICE
625 ppm: two males died
control: one female died - Body weight and weight changes:
- no effects observed
- Food consumption and compound intake (if feeding study):
- no effects observed
- Food efficiency:
- not examined
- 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):
- RATS
625 ppm: MCH in males decreased, PLT count increased, PT decreased in females
MICE
625 ppm: increased reticulocyte counts in males
250 ppm: increased leukocyte (WBC) counts in males
100 ppm: PLT count decreased in males - Clinical biochemistry findings:
- effects observed, treatment-related
- Description (incidence and severity):
- RATS
625 ppm: AST and ALT increased in males, and increased ALT in females. BUN levels increased in males. ALP levels decreased in females
250 ppm: AST and ALT increased in males, ALP levels increased in males
MICE (effects observed, non-treatment-related)
625 ppm: decreased total bilirubin levels in males, BUN levels increased in males, TCHO increased in females
250 ppm: decreased ALP levels in males - 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):
- RATS
625 ppm: absolute and relative weights of the liver in males increased, relative weight of spleen in males increased, absolute weight of kidney increased in males
250 ppm: relative weight of the liver in males increased, relative weight of spleen in females increased
Females did not show a statistical significance increase in liver weights but showed a dose-dependent increase
MICE (effects observed, non-treatment-related)
650 ppm: absolute and relative liver weights increased in males, absolute liver weight increased in females, absolute kidney weight increased in males
250 ppm: relative kidney weight increased in females - Gross pathological findings:
- effects observed, non-treatment-related
- Description (incidence and severity):
- RATS
625 ppm: white focal lesions in lungs of males
250 ppm: adhesions in the accessory lobe of the liver and right kidney in females
MICE
625 ppm: In two dead males, a black spot lesion of the stomach, small of spleen, and thymus were observed. A nodule was noted in thoracic muscle of one male
Control: small of the thymus in a dead female
No abnormal findings related to the test chemical were observed in the animals that survived until the scheduled terminal necropsy. - Neuropathological findings:
- not examined
- Histopathological findings: non-neoplastic:
- effects observed, treatment-related
- Description (incidence and severity):
- RATS
625 ppm: indicative of alveolar macrophage aggregation in males, four cases of bile duct hyperplasia in the liver of male animals
250 ppm: adhesion of hepatocytes to the renal capsule and atrophy of the glomeruli and tubules in the renal cortex in females. Two cases of bile duct hyperplasia in the liver of male animals
Males showed hyaline droplet accumulation in the distal convoluted tubule and cortical tubular basophilia in the kidney. Hyaline droplet accumulation was observed in all test groups including the control groups. However, the extent increased in a concentrationdependent manner.
Tubular basophilia in the renal cortex had known a spontaneous lesion due to aging in the rats and was exacerbated by the test substance. The severity of tubular basophilia increased upon exposure to cyclohexanone in a dosedependent manner. Therefore, it was considered that tubular basophilia in the renal cortex may be aggravated by the progression of chronic progressive nephropathy due to cyclohexanone exposure
MICE (effects observed, non-treatment-related)
625 ppm: atrophy of the liver, spleen, and thymus and single-cell necrosis of the liver and erosion of the glandular stomach in the dead males
Control: atrophy of the liver, spleen, and thymus and single-cell necrosis of the liver in the dead female
No abnormal findings related to the test chemical were observed in the animals that survived until the scheduled terminal necropsy.
Effect levels
open allclose all
- Dose descriptor:
- NOAEL
- Remarks:
- rats
- Effect level:
- 100 ppm
- Based on:
- test mat.
- Sex:
- male
- Basis for effect level:
- clinical biochemistry
- histopathology: non-neoplastic
- Dose descriptor:
- NOAEL
- Remarks:
- mice
- Effect level:
- > 625 ppm
- Based on:
- test mat.
- Sex:
- male/female
- Basis for effect level:
- other: no adverse effects observed
Target system / organ toxicity
open allclose all
- Critical effects observed:
- yes
- Lowest effective dose / conc.:
- 250 ppm
- System:
- hepatobiliary
- Organ:
- liver
- Treatment related:
- yes
- Dose response relationship:
- yes
- Critical effects observed:
- yes
- Lowest effective dose / conc.:
- 250 ppm
- System:
- urinary
- Organ:
- kidney
- Treatment related:
- yes
- Dose response relationship:
- yes
Any other information on results incl. tables
Mean ± standard deviation values for the cyclohexanone concentrations in the inhalation chambers were 99.51 ± 4.63 ppm, 252.87 ± 8.38 ppm, and 625.32 ± 35.48 ppm for rats, and 103.63 ± 26.97 ppm, 251.36 ± 38.49 ppm, and
617.83 ± 86.41 ppm for mice throughout the 13-week exposure period. Deviations in the mean observed concentrations from the target concentrations were less than 11.5%.
Applicant's summary and conclusion
- Conclusions:
- In conclusion, inhalation exposure to cyclohexanone vapors for 13 weeks induced hepatoxicity and renal toxicity in rats of both sexes. The authors concluded on a NOAEL of 100 ppm for the hepatic endpoint in F344 rats and >625 ppm in B6C3F1 mice.
- Executive summary:
In this study, ten male and ten female rats (F344) and mice (B6C3F1) per group were exposed to cyclohexanone vapors at 100, 250, and 625 ppm concentrations for 6 h per day, 5 d per week, and for 13 weeks. Clean air was used as negative control. All rats and mice were killed after the exposure period. Clinical signs, body weight, feed intake, and ophthalmoscopy findings were recorded during the exposure period, and hematology, blood biochemistry, organ weights, gross findings, and histopathology were evaluated thereafter.
The following effects were recorded in cyclohexanone-exposed F344 rats: increased alanine aminotransferase (ALT) and aspartate aminotransferase (AST) levels, increased liver weight, and bile duct hyperplasia in the males exposed to 250 and 625ppm cyclohexanone, increased ALT levels and bile duct hyperplasia in the females exposed to 625ppm cyclohexanone, and increased blood urea nitrogen (BUN) and tubular basophilia in the renal cortex in the males exposed to 625 ppm cyclohexanone.
B6C3F1 mice exposed to cyclohexanone showed no obvious exposure-related effects.
Based on the findings in male rats, the NOAEL (rats) was set at 100 ppm and the NOAEL (mice) greater than 625 ppm.
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