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EC number: 222-376-7 | CAS number: 3452-97-9
- 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
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- 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:
- short-term repeated dose toxicity: oral
- Remarks:
- combined repeated dose and reproduction / developmental screening
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- other: Guideline study (SIDS documents; Iuclid reference [28]; Reliability assigned: 1)
Cross-reference
- Reason / purpose for cross-reference:
- reference to same study
Data source
Referenceopen allclose all
- Reference Type:
- publication
- Title:
- Unnamed
- Year:
- 2 007
- Report date:
- 2007
- Reference Type:
- other: summary of toxicity studies
- Title:
- Unnamed
- Year:
- 2 007
- Report date:
- 2007
- Reference Type:
- secondary source
- Title:
- Unnamed
- Year:
- 1 997
- Report date:
- 1997
Materials and methods
Test guideline
- Qualifier:
- equivalent or similar to guideline
- Guideline:
- OECD Guideline 422 (Combined Repeated Dose Toxicity Study with the Reproduction / Developmental Toxicity Screening Test)
- Deviations:
- no
- GLP compliance:
- yes
- Limit test:
- no
Test material
- Reference substance name:
- 3,5,5-trimethylhexan-1-ol
- EC Number:
- 222-376-7
- EC Name:
- 3,5,5-trimethylhexan-1-ol
- Cas Number:
- 3452-97-9
- Molecular formula:
- C9H20O
- IUPAC Name:
- 3,5,5-trimethylhexan-1-ol
- Details on test material:
- - Source: KYOWA HAKKO KOGYO CO., LTD.
- Analytical purity: 92.7 %
- Lot/batch No.: 70713
Constituent 1
Test animals
- Species:
- rat
- Strain:
- Crj: CD(SD)
- Sex:
- male/female
- Details on test animals or test system and environmental conditions:
- TEST ANIMALS
- Source: no data
- Age at study initiation: 10 weeks
- Weight at study initiation: 335-399g for males,204-260g for females
Administration / exposure
- Route of administration:
- oral: gavage
- Vehicle:
- olive oil
- Details on oral exposure:
- PREPARATION OF DOSING SOLUTIONS:
Isononanol was dissolved in olive oil to give concentrations of 0.24, 1.2, and 6 % weight/volume.
New solutions were prepared every 7 days.
DIET PREPARATION
- Rate of preparation of diet (frequency): n.a.
- Mixing appropriate amounts with (Type of food): n.a.
- Storage temperature of food: n.a.
VEHICLE
- vehicle: olive oil
- Justification for use and choice of vehicle: test substance insoluble in water
- Concentration in vehicle: 0.24, 1.2, and 6 % weight/volume
- Amount of vehicle (if gavage): 5 mL/kg bw
- Lot/batch no. Yakuhan Pharmaceutical Ltd.
- Purity: Japan Pharmacopoiea - Analytical verification of doses or concentrations:
- not specified
- Duration of treatment / exposure:
- Males 46 days, females 14 days before mating to day 3 of lactation
- Frequency of treatment:
- once daily
Doses / concentrations
- Remarks:
- Doses / Concentrations:
0 (vehicle) , 12, 60, 300 mg/kg bw/day
Basis:
actual ingested
- No. of animals per sex per dose:
- 12
- Control animals:
- yes, concurrent vehicle
- Details on study design:
- - Dose selection rationale: based on range finding study at 100, 300, and 1000 mg/kg bw using groups of 5 male and 5 female rats at each dose level, 300 mg/kg bw was selected as the top dose which was expected to be clearly toxic. Lower doses were calculated using a factor of 5.
- Rationale for animal assignment: random
- Rationale for selecting satellite groups: no satellite group
- Post-exposure recovery period in satellite groups: n.a.
- Section schedule rationale: random - Positive control:
- no
Examinations
- Observations and examinations performed and frequency:
- CAGE SIDE OBSERVATIONS: Yes
- Time schedule: daily
- Cage side observations checked in table [No.?] were included.
DETAILED CLINICAL OBSERVATIONS: No data
BODY WEIGHT: Yes
- Time schedule for examinations:
males: prior to administration of drug, on days 2, 5, 7, 10 and 14 of administration of the drug and thereafter every 7 days (including the final day of treatment) as well as on the day of the necropsies
females: on days 0, 1, 3, 5, 7, 10, 14, 17 and 20 of gestation, days 0, 1, and 4 of nursing
FOOD CONSUMPTION AND COMPOUND INTAKE (if feeding study):
- Food consumption for each animal determined and mean daily diet consumption calculated as g food/kg body weight/day: No data; Food consumption was determined weekly
- Compound intake calculated as time-weighted averages from the consumption and body weight gain data: n.a.
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: no data provided, but can easily be calculated from the body weight gain and feed intake data.
WATER CONSUMPTION AND COMPOUND INTAKE (if drinking water study): n.a.
- Time schedule for examinations: water consumption was determined weekly
OPHTHALMOSCOPIC EXAMINATION: No
HAEMATOLOGY: Yes
- Time schedule for collection of blood: at termination, day 46 of exposure
- Anaesthetic used for blood collection: No data
- Animals fasted: No data
- How many animals: 12 per dose group
- Parameters checked in table [No. 5 of the report] were examined: erythrocyte count, mean erythrocyte capacity, platelet count, leucocyte count, hemoglobin, mean erythrocyte hemoglobin amount as well as leucocyte percentage. Coagulation time.
CLINICAL CHEMISTRY: Yes
- Time schedule for collection of blood: day 46 (males)
- Animals fasted: for 16 hours
- How many animals: 12 per dose group
- Parameters: serum GOT and GPT, γ GTP, cholinesterase, blood sugar, total cholesterol, triglycerides, phospholipids, bilirubin, urinary nitrogen, creatinine, calcium, inorganic phosphorus, total protein and albumin, sodium and potassium, chloride , A/G ration, protein fractionation
URINALYSIS: Yes
- Time schedule for collection of urine: day 43 to 44
- Animals: 6 males/group
- Parameters: pH, protein, sugar, ketones, urobilinogen, bilirubin, occult blood reaction, sediment, specific gravity and urinary volume (capacity).
NEUROBEHAVIOURAL EXAMINATION: No
OPTHER
- Necropsy
- Organs examined at necropsy:
a) macroscopic: organ weight: liver, kidney, adrenal, thymus, testes,(epidymis)
b) microscopic: all animals.
- Sacrifice and pathology:
- GROSS PATHOLOGY: Yes;
Organ weight: liver, kidney, adrenal glands, thymus, testes, epididymis and ovaries
HISTOPATHOLOGY: Yes; all animals
Organs: liver, kidneys, pancreas, heart, lungs, brain, pituitary gland, thymus, adrenal glands, thyroid gland, stomach (anterior stomach • glandular stomach ), duodenum, jejunum, ileum, cecum, rectum, prostate gland and ovaries, testes and epididymis - Statistics:
- No data
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
- Food efficiency:
- not specified
- 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:
- no effects observed
- Details on results:
- CLINICAL SIGNS AND MORTALITY
In the 300 mg/kg group one female died on day 21 of gestation, and three others had to be killed because of weakness from days 14 to 19 of
gestation. In these animals, body weights and food consumption were decreased, and histopathological examination revealed periportal fatty
change in the liver, renal epithelial fatty change and other lesions.
BODY WEIGHT AND WEIGHT GAIN
Food consumption was increased and body weights tended to be increased in males of the 300 mg/kg group, but the opposite was the case for females receiving the highest dose.
FOOD CONSUMPTION AND COMPOUND INTAKE (if feeding study)
Food consumption was increased and body weights tended to be increased in males of the 300 mg/kg group, but the opposite was the case for females receiving the highest dose.
FOOD EFFICIENCY
No data
WATER CONSUMPTION AND COMPOUND INTAKE (if drinking water study)
n.a.
OPHTHALMOSCOPIC EXAMINATION
Not examined
HAEMATOLOGY
Slight decreases in red blood cell counts, hematocrit, hemoglobin concentrations in males of the 300 mg/kg group.
CLINICAL CHEMISTRY
Biochemical examinations revealed slight decreases in BUN and chloride in males of the 300 mg/kg group.
URINALYSIS
Urinalysis revealed increases in urine volume and water consumption in males of the 300 mg/kg group.
NEUROBEHAVIOUR
Not examined
ORGAN WEIGHTS
Liver: absolute liver weights were increased in males and females of the 300 mg/kg group, relative liver weights were increased in males and females of the 60 and 300 mg/kg groups.
Kidney: absolute and relative weights of the right and left kidneys were increased in males of the 60 and 300 mg/kg groups, and relative weights of the right and left kidneys were increased in females of the 300 mg/kg group.
GROSS PATHOLOGY
Autopsy revealed pale discoloration of the kidneys in males of the 60 and 300 mg/kg groups, swelling of the kidneys in males of the 300 mg/kg group, and yellowish white discoloration of the liver in females of the 300 mg/kg group.
HISTOPATHOLOGY: NON-NEOPLASTIC
Histopathological examination revealed in male of the more than 12 mg/kg group, a slight or moderate degree of hyaline droplet and eosinophilic body in proximal tubular epithelium in kidney, but these findings were not observed in female (alpha2u-Globulin Nephropathy).
- In males, a slight or moderate degree of renal tubular epithelial regeneration and formation of granular casts in kidneys in males of the 60 and 300 mg/kg groups,
- - a slight degree of irregularity in the shape of follicles, columnar change of follicular epithelium and decrease in colloid in the thyroid were observed in males of the 300 mg/kg group.
- In female rats, a slight degree of renal epithelial fatty change in females of the 60 and 300 mg/kg groups, and atrophy of the thymus in the 300 mg/kg group.
HISTOPATHOLOGY: NEOPLASTIC (if applicable)
No data
HISTORICAL CONTROL DATA (if applicable)
No data
Effect levels
open allclose all
- Dose descriptor:
- NOAEL
- Effect level:
- 12 mg/kg bw/day (actual dose received)
- Sex:
- male/female
- Basis for effect level:
- other: no effect noted
- Dose descriptor:
- LOAEL
- Effect level:
- 60 mg/kg bw/day (nominal)
- Sex:
- male/female
- Basis for effect level:
- other: males: liver and kidney weight increased; histopathological changes in liver and kidney. Females: histopathological kidney changes.
Target system / organ toxicity
- Critical effects observed:
- not specified
Any other information on results incl. tables
Dose level(mg/kg/day) |
||||
Haematology |
0 |
12 |
60 |
300 |
No. of animals |
12 |
12 |
12 |
12 |
Hematocrit (%) |
52.6 ±1.89 |
52.6 ±2.90 |
52.4 ±2.59 |
49.9* ±2.25 |
Hemoglobin (g/dl) |
16.4 ±0.63 |
16.2 ±0.68 |
15.7 ±0.68 |
15.3** ±0.68 |
Blood chemical |
||||
BUN (mg/dl) |
15.67 ±1.87 |
15.63 ±1.45 |
16.22 ±1.66 |
13.87* ±1.89 |
Cl(mEq/l) |
107.3 ±1.3 |
106.5 ±2.4 |
106.2 ±1.6 |
104.8** ±0.6 |
Organ weights, Males absolute organ weight |
||||
Liver (g) |
12.120 ±1.468 |
12.953 ±2.178 |
13.676 ±1.136 |
17.815** ±1.723 |
Kidney (right, g) |
1.570 ±0.120 |
1.602 ±0.166 |
1.771* ±0.196 |
1.918** ±0.205 |
Kidney (left, g) |
1.540 ±0.092 |
1.58 ±0.184 |
1.744** ±0.186 |
1.906** ±0.232 |
relative organ weight |
||||
Liver (g) |
2.431 ±0.162 |
2.559 ±0.227 |
2.780** ±0.126 |
3.493** ±0.207 |
Kidney (right, g) |
0.316 ±0.018 |
0.318 ±0.022 |
0.362* ±0.043 |
0.378** ±0.043 |
Kidney (left, g) |
0.310 ±0.018 |
0.317 ±0.031 |
0.357** ±0.043 |
0.375** ±0.053 |
Organ weights, Females absolute organ weight |
||||
Liver (g) |
13.222 ±1.105 |
13.470 ±1.142 |
14.384 ±1.673 |
16.032** ±1.340 |
relative organ weight |
||||
Liver (g) |
4.011 ±0.191 |
4.056 ±0.219 |
4.408* ±0.425 |
5.330** ±0.390 |
Kidney (right, g) |
0.299 ±0.050 |
0.299 ±0.016 |
0.295 ±0.022 |
0.330* ±0.030 |
Kidney (left, g) |
0.295 ±0.052 |
0.289 ±0.019 |
0.291 ±0.025 |
0.328* ±0.036 |
Values are expressed as Mean±S.D.
Significantly different from 0 mg/kg bw/day group: * p=0.05 ** p=0.01
----------------------------------------------------------------------------
Dose level(mg/kg/day) |
||||
Histopathology, Males |
0 |
12 |
60 |
300 |
No. of animals |
12 |
12 |
12 |
12 |
Kidney |
||||
Hyaline droplet, proximal tubular epithelium |
1 |
9** |
12** |
12** |
Eosinophilic body, proximal tubular epithelium |
0 |
9** |
11** |
12** |
Regeneration, tublar epithelium |
0 |
1 |
6* |
7* |
Cast, granular |
0 |
0 |
3 |
6* |
ThyroidDecrease, colloid |
0 |
0 |
0 |
4 |
Histopathology, Females |
||||
Kidney |
||||
Hyaline droplet, proximal tubular epithelium |
0 |
0 |
0 |
0 |
Eosinophilic body, proximal tubular epithelium |
0 |
0 |
0 |
0 |
Degeneration, fatty, proximal tubular epithelium |
0 |
0 |
0 |
3 |
ThyroidDecrease, colloid |
0 |
0 |
0 |
0 |
Thymus Atrophy |
0 |
0 |
0 |
3 |
Values are no. of animals with findings.
Significantly different from 0 mg/kg bw/day group: * p=0.05 ** p=0.01
Applicant's summary and conclusion
- Conclusions:
- The NOAEL of 3,5,5-trimethylhexan-1-ol for parental animals was 12 mg/kg bw/day for males and for females in a combined repeat dose/reproduction-developmental toxicity study (OECD TG 422). The LOAEL was 60 mg/kg bw/day for males and females.
- Executive summary:
3,5,5-trimethylhexan-1-ol was tested in a combined repeat dose/reproduction-developmental toxicity screening study according to OECD TG 422 and under GLP conditions using male and female rats at dose levels of 0, 12, 60, and 300 mg/kg bw/day. Key findings in parental animals by dose group were as follows:
12 mg/kg bw/day: no effects in male or female rats
60 mg/kg bw/day:
- significantly (p<0.05) increased absolute or relative organ weights (liver, kidney) in males and females
- a slight or moderate degree of hyaline droplet and eosinophilic body in proximal tubular epithelium in kidney, but these findings were not observed in female (alpha2µ-Globulin Nephropathy). However, alpha2µ-Globulin Nephropathy appears to be sex- and species -specific. That is, it occurs in male rats but not female rats and in mice, rabbit, guinea pigs or human. because they do not produce alpha2µ-Globulin.
- a slight or moderate degree of renal tubular epithelial regeneration and formation of granular casts in kidneys in males
300 mg/kg bw/day:
- one female died and 3 were moribund; deaths ocurred at gestation days 14 -21
- tendency of increased body weight in males and decreased body weight in females, compared to controls
- food consumption increased in males, decreased in females
- significant (p<0.05), yet small hematological changes; substantiated by small decreases of hematocrit and hemoglobin
- significantly increased blood urea nitrogen (p<0.05) and serum chloride (p<0.05) at termination
- increased absolute and relative liver and kidney weights in males and females (p<0.01)
- decrease of thyroid colloid in 4/12 males
- thymus atrophy in 3/12 females
Target organs:
Liver: periportal adiposis in males and females at 60 and 300 mg/kg bw/day,
Kidneys: mild fatty urethral tubular epithelium degeneration in males and females at 60 and 300 mg/kg bw/day (MHLW 1997).
On the basis of these findings, the NOAEL of 3,5,5-trimethylhexan-1-ol for repeat dose toxicity was considered to be 12 mg/kg/day for males and for females; the LOAEL was 60 mg/kg bw/day (MHLW, 1997, Yoshimura 2007).
The study is considered to be suitable for assessment. It should, however, be noted that compared to the more specific guideline studies for this endpoint (e.g. OECD 408) the list of parameters to be examined is reduced. Further, the animal number is relatively low in screening studies and the statistical power is therefore reduced compared to an OECD 408 study. In some instances borderline effects may therefore fail to gain a level of statistical significance, making it difficult to assign correctly NOAEL-values.
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