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EC number: 234-294-9 | CAS number: 11071-47-9
- 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
- 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
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Repeated dose toxicity: inhalation
Administrative data
- Endpoint:
- repeated dose toxicity: inhalation
- 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: GLP compliant, guideline study, available as published report, no restrictions, fully adequate for assessment
Cross-reference
- Reason / purpose for cross-reference:
- reference to same study
Data source
Reference
- Reference Type:
- study report
- Title:
- Unnamed
- Year:
- 2 007
- Report date:
- 2007
Materials and methods
Test guidelineopen allclose all
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 422 (Combined Repeated Dose Toxicity Study with the Reproduction / Developmental Toxicity Screening Test)
- Deviations:
- yes
- Remarks:
- Males and females were exposed to the test substance for 10 weeks prior to pairing.
- Qualifier:
- equivalent or similar to guideline
- Guideline:
- OECD Guideline 413 (Subchronic Inhalation Toxicity: 90-Day Study)
- Deviations:
- yes
- Remarks:
- Males and females were paired for mating. Females were pregnant prior to termination.
- GLP compliance:
- yes (incl. QA statement)
- Limit test:
- no
Test material
- Reference substance name:
- Isooctene
- EC Number:
- 234-294-9
- EC Name:
- Isooctene
- Cas Number:
- 11071-47-9
- Molecular formula:
- C8H16
- IUPAC Name:
- 2-methylhept-1-ene
- Details on test material:
- - Name of test material (as cited in study report): isooctene
- Synonym: Di-n-butene
- Physical state: Clear, colourless liquid
- Analytical purity: 99.9%, 99.84% area (gas chromatography)
- Lot/batch No.: K402 distillate
- Expiration date of the lot/batch: Unlimited
- Stability under test conditions: Unlimited
- Storage condition of test material: room temperature; air sensitive, under N2
Constituent 1
Test animals
- Species:
- rat
- Strain:
- Wistar
- Sex:
- male/female
- Details on test animals or test system and environmental conditions:
- TEST ANIMALS
- Source: Charles River Laboratories, Research Models and Services, Germany GmbH; Sandhofer Weg 7, 97633 Sulzfeld
- Age at study initiation: Approximately 6 weeks
- Weight at study initiation: group mean range 161.7-166.6 g (males), 126.1-131.0 g (females)
- Housing: Individually in wire cages
- Diet: Milled mouse/rat laboratory diet (Provimi Kliba SA, Kaiseraugst, Basel Switzerland) ad libitum except during exposure and motor activity measurements
- Water: tap water ad libitum except during exposure and motor activity measurements
- Acclimation period: Approximately two weeks
ENVIRONMENTAL CONDITIONS
- Temperature: 20-24°C
- Humidity: 30-70%
- Air changes (per hr): Not reported; air-conditioned
- Photoperiod: 12 hrs dark / 12 hrs light
IN-LIFE DATES: From: 13 June 2006 To: 26 April 2007
Administration / exposure
- Route of administration:
- inhalation: vapour
- Type of inhalation exposure:
- whole body
- Vehicle:
- other: air
- Remarks on MMAD:
- MMAD / GSD: Not applicable
- Details on inhalation exposure:
- GENERATION OF TEST ATMOSPHERE / CHAMBER DESCRIPTION
- Exposure apparatus: glass-steel inhalation chamber, volume of about 1.4 m³ (BASF Aktiengesellschaft).
- Air flow: Approximately 20 per hour
- Air conditions: Test group 0: A positive pressure was maintained by adjusting the airflow of the exhaust air system. This ensured that no laboratory air reached the control animals.
Test groups 1 - 3: A negative pressure was maintained by adjusting the airflow of the exhaust air system. This ensured that the laboratory was not contaminated as the result of any leakage from the inhalation chamber.
- System of generating particulates/aerosols: For each concentration the test substance was supplied to a thermostated vaporizer at a constant rate by means of the metering pump.
- Temperature, humidity, pressure in air chamber: The vapour was generated with conditioned supply air (actual range 54.6-61.1% relative humidity, temperature 20.9-22.7°C) and passed into the inhalation system.
TEST ATMOSPHERE
- Brief description of analytical method used: The nominal concentration was calculated from the study means of the test pump rates and the supply airflows used during exposure to generate the respective concentrations.
The concentrations of the inhalation atmospheres were analyzed by gas chromatography in all test groups including control.
- Total hydrocarbon analyzers were used to continuously monitor the constancy of concentrations of test substance vapours in the inhalation systems.
- No surveillance of the oxygen content in the inhalation system was performed. The air change within the inhalation systems was judged to be sufficient to prevent oxygen depletion by the breathing of the animals and the concentrations of the test substance used could not have a substantial influence on oxygen partial pressure. - Analytical verification of doses or concentrations:
- yes
- Details on analytical verification of doses or concentrations:
- The vapour generation effectiveness was as expected for these high concentrations (range of 83.9-88.8%). Real time surveillance of the inhalation atmospheres with total hydrocarbon analyzers generally proved the constancy of each concentration throughout the daily exposures.
- Duration of treatment / exposure:
- 6 hours per day / 5 days per week
- Frequency of treatment:
- Males were treated for approx. 13 weeks (10 weeks premating, 3 weeks mating and post mating). In females treatment was performed during premating (10 weeks), mating and gestation through day 4 after delivery (approx. 15 weeks).
Doses / concentrationsopen allclose all
- Remarks:
- Doses / Concentrations:
1000, 5000 and 15000 mg/m3
Basis:
other: target concentration
- Remarks:
- Doses / Concentrations:
1200, 5600 and 16900 mg/m3
Basis:
nominal conc.
- Remarks:
- Doses / Concentrations:
1000±100 , 50000±200 and 14900±700 mg/m3
Basis:
analytical conc.
- No. of animals per sex per dose:
- 10
- Control animals:
- yes, sham-exposed
- Details on study design:
- - Dose selection rationale: as requested by the sponsor
Examinations
- Observations and examinations performed and frequency:
- CAGE SIDE OBSERVATIONS: Yes
- Time schedule: The clinical conditions of the test animals were recorded at least 3 times (before, during and after exposure) on exposure days and once during the preflow period, on the day of neurofunctional test and prior to gross necropsy. During exposure only a group wise examination was possible.
DETAILED CLINICAL OBSERVATIONS: Yes
- Time schedule: Detailed clinical observations were performed in all animals prior to the exposure period and thereafter in weekly intervals.
BODY WEIGHT: Yes
- Time schedule for examinations: The body weight of all parental animals was determined on day -5 (start preflow period), on day 0 (start exposure period) and then in weekly intervals as well as prior to gross necropsy.
FOOD CONSUMPTION:
- Food consumption for each animal determined and mean daily diet consumption calculated as g food/kg body weight/day: Yes, with the following exceptions; Food consumption was not determined during the mating period
Food consumption of the parental females with evidence of sperm (p.c.) was determined for days 0-7, 7-14 and 14-20 p.c.
Food consumption of parental females, which gave birth to a litter was determined for days 1-4 post partum (p.p.)
FOOD EFFICIENCY:
- Food efficiency (group means) was calculated based upon individual values for body weight and food consumption.
OPHTHALMOSCOPIC EXAMINATION: Yes
- Before the start of the exposure period (day -3) the eyes of all animals, and at the end of the study (day 88 for the parental male animals and day 102 for the parental female animals) the eyes of the animals of test group 0 (control group) and test group 3 (high concentration) were examined with an ophthalmoscope (HEINE Optotechnik, Herrsching, FRG)) for any changes in the refracting media.
HAEMATOLOGY: Yes
- Time schedule for collection of blood: Towards the end of the premating period, blood was taken from the retro-orbital venous plexus
- Anaesthetic used for blood collection: Yes (Isoba®, Essex GmbH Munich, Germany)
- Animals fasted: Yes
- How many animals: 10 animals per test group and sex.
- Parameters examined: leukocyte count, erythrocyte count, haemoglobin, haematocrit, mean corpuscular volume, mean corpuscular haemoglobin, mean corpuscular haemoglobin concentration, platelet count, differential blood count and reticulocyte count.
CLINICAL CHEMISTRY: Yes
- Time schedule for collection of blood: Towards the end of the premating period, blood was taken from the retro-orbital venous plexus
- Animals fasted: Yes
- How many animals: 10 animals per test group and sex.
- Parameters examined: alanine aminotransferase, aspartate aminotransferase, alkaline phosphatase and γ-glutamyltransferase, sodium, potassium, chloride, inorganic phosphate, calcium, urea, creatinine, glucose, total bilirubin, total protein, albumin, globulins, triglycerides, cholesterol and magnesium.
URINALYSIS: No
NEUROBEHAVIOURAL EXAMINATION: Yes
- Time schedule for examinations: A functional observational battery (FOB) and measurements of motor activity (MA) were carried out on study days 50 and 51 for males and females, respectively.
- Dose groups that were examined: From each concentration group, neurofunctional tests were performed in five male and five female animals.
- Battery of functions tested: sensory activity / grip strength / motor activity - Sacrifice and pathology:
- GROSS PATHOLOGY: Yes; a complete necropsy including gross pathological evaluation and weighing of selected organs (adrenals, brain, heart, kidneys, liver, lungs, ovaries, spleen, thymus, uterus, epididymides and testes) was performed.
HISTOPATHOLOGY: Yes; the following organs and tissues were examined histopathologically: all gross lesions, brain, spinal cord (cervical, thoracic and lumbar), sciatic nerve, pituitary gland, salivary glands, thyroid/parathyroid glands, adrenal glands, prostate gland, seminal vesicles, coagulation glands, uterus, oviducts, vagina, female mammary gland, thymus, lymph nodes, spleen, trachea, lungs, heart, aorta, liver, pancreas, kidneys, oesophagus, stomach, duodenum, jejunum, ileum, caecum, colon, rectum, urinary bladder, sternum with marrow, bone marrow (femur), head (with nasal cavities), larynx, pharynx, eyes with optic nerve, femur with knee joint, skin, skeletal muscle, extraorbital lachrymal glands).
In addition, to examine whether there were treatment-related accumulation of alpha-2u-globulin in the kidneys of male animals, the slides were stained according to Mallory-Heidenhain. Based on these results, the kidneys of one male animal of each concentration group was stained immunohistochemically. - Other examinations:
- After ten weeks of exposure, the parental animals were mated to produce a litter. Mating pairs were formed from the same concentration group. The parental animals were examined for their mating and reproductive performances. The pups were sexed and were weighed on the day after birth and on day 4 post partum. Their viability was recorded. All pups were underwent necropsy on day 4 post partum and were examined macroscopically for external and visceral findings.
- Statistics:
- Means and standard deviations of each test group were calculated for parameters measured. Further statistical analyses were performed as appropriate, according to the methods of Dunnett’s t-test (two-sided), Fisher’s Exact test, Wilcoxon test (one-sided), and/or Kruskal-Wallis test (two-sided).
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 consumption and compound intake (if feeding study):
- effects observed, treatment-related
- Food efficiency:
- effects observed, treatment-related
- Water consumption and compound intake (if drinking water study):
- not examined
- Ophthalmological findings:
- no effects observed
- Haematological findings:
- effects observed, treatment-related
- Clinical biochemistry findings:
- effects observed, treatment-related
- Urinalysis findings:
- not examined
- Behaviour (functional findings):
- no effects observed
- Organ weight findings including organ / body weight ratios:
- effects observed, treatment-related
- Gross pathological findings:
- no effects observed
- Histopathological findings: non-neoplastic:
- effects observed, treatment-related
- Histopathological findings: neoplastic:
- no effects observed
- Details on results:
- CLINICAL SIGNS AND MORTALITY
There was no mortality. Clinically, slight ataxia (from day 9 onward) and salivation (from day 8 onward) were observed at 15000 mg/m3 indicating marginal irritation and systemic toxicity of Isooctene.
BODY WEIGHT AND WEIGHT GAIN
In male animals the mean body weight and body weight change were found to be significantly decreased when compared with the controls.
FOOD CONSUMPTION
A transient decrease of food consumption was observed in male and female animals on study day 7, which did not occur again after the animals adjusted to the test substance and the exposure procedure.
FOOD EFFICIENCY
In male animals, food efficiency was found to be significantly decreased when compared with the controls.
HAEMATOLOGY
After inhalation of the substance for about 2 months there was noticed a slight increase of the median of the platelet counts in the parent males exposed to 15000 mg/m3.
The median of the prothrombin time was decreased in the male parents beginning in group 2 (5000 mg/m3), and in the female parents in the group exposed to 15000 mg/m3, only.
CLINICAL CHEMISTRY
In the female parents of the 15000 mg/m3 group the median of the aspartate aminotransferase activity was decreased after 2 months of substance inhalation, in the male parents of the same dose group there was assessed an increased median of the alanine aminotransferase activity. The median of the γ-glutamyltransferase activity was slightly increased in the 15000 mg/m3 group of the rats of both sexes, but this was only statistically significant in the males.
In the male rats the median of the total protein levels was increased beginning in the 5000 mg/m3 dose group. Regarding the medians of the protein fractions albumin and globulin the significant increase was only assessed in the 15000 mg/m3 dose group. The median of the globulin fraction was increased in the female rats of the 15000 mg/m3 dose group, too. The male parents showed increased medians of the bilirubin concentration in the 15000 mg/m3 dose group, and decreased medians of the glucose levels starting in the 5000 mg/m3 dose group. The medians of the cholesterol values were increased in the rats of both sexes beginning in the 5000 mg/m3 dose groups. The median of the triglyceride concentration was increased in the 15000 mg/m3 dose group of the females, only. In this group, there was found a decrease of the urea and the creatinine concentration, too.
The medians of the potassium and calcium serum levels were increased in the rats of both sexes (potassium: males beginning in the 5000 mg/m3, and in the females in the 15000 mg/m3 dose group; calcium: in the 15000 mg/m3 dose group of both sexes). The magnesium levels were increased only in the male parents beginning in the 1000 mg/m3 dose group. The increase in the low-concentration group was still within the range of biological variations. Therefore, this is not regarded as a toxicologically relevant effect.
ORGAN WEIGHTS
Absolute- and relative liver and kidney weights of males were significantly increased in animals exposed to 5000 and 15000 mg Isooctene/m3
HISTOPATHOLOGY: NON-NEOPLASTIC
The treatment-related microscopic changes observed were increased hyaline cast(s) and basophilic cortical tubules in the kidneys of male animals from group 2 (5000 mg/m3) onward. In addition, in males there was suspected greater propensity for the development of large hyaline droplets related to the proximal tubules compared to controls. Mallory-Heidenhain stain of all male kidneys and immunhistochemistry of selected male kidneys with an alpha 2u globulin antibody revealed a concentration-dependent accumulation of alpha 2u globulin in cortical tubular cells in all treated groups. However, in the absence of any treatment-related morphological signs of cytotoxicity, the minimal to slight accumulation of alpha 2u globulin in the group 1000 mg/m3 males is regarded to be adaptive and non-adverse in character.
In the respiratory tract no signs of toxicity were observed.
Effect levels
- Dose descriptor:
- NOAEC
- Effect level:
- 1 000 mg/m³ air (analytical)
- Sex:
- male/female
- Basis for effect level:
- other: see 'Remark'
Target system / organ toxicity
- Critical effects observed:
- not specified
Any other information on results incl. tables
Intergroup comparison of bodyweights (g) selected timepoints
|
males |
females |
||||||
|
Dose level of isooctane (mg/m3) |
|||||||
Day |
0 |
1000 |
5000 |
15000 |
0 |
1000 |
5000 |
15000 |
0 |
166.6 |
163.3 |
162.0 |
161.7 |
131.1 |
126.1 |
129.1 |
129.3 |
21 |
289.8 |
276.5 |
277.9 |
261.0** |
185.0 |
182.8 |
188.3 |
183.2 |
49 |
373.3 |
355.0 |
355.2 |
328.2** |
219.1 |
219.1 |
224.9 |
217.8 |
91 |
422.0 |
406.1 |
403.0 |
371.3** |
- |
- |
- |
- |
105 |
- |
- |
- |
- |
270.3 |
258.8 |
273.7 |
263.4 |
*p<=0.05 **p<=0.01
Intergroup comparison of food efficiency, selected timepoints
|
males |
females |
||||||
|
Dose level of isooctane (mg/m3) |
|||||||
Day |
0 |
1000 |
5000 |
15000 |
0 |
1000 |
5000 |
15000 |
7 |
27.1 |
27.8 |
28.5 |
24.2* |
16.5 |
19.4 |
17.3 |
17.6 |
28 |
15.9 |
15.9 |
14.3 |
11.8** |
9.5 |
7.1 |
8.6 |
9.2 |
63 |
7.4 |
6.4 |
7.7 |
5.6 |
3.9 |
6.4 |
7.4 |
3.3 |
*p<=0.05 **p<=0.01
Intergroup comparison of selected organ weights (g)
|
males |
females |
||||||
|
Dose level of isooctane (mg/m3) |
|||||||
|
0 |
1000 |
5000 |
15000 |
0 |
1000 |
5000 |
15000 |
Kidney, abs |
2.377 |
2.411 |
2.717* |
2.837** |
1.751 |
1.758 |
1.814 |
1.826 |
Kidney, rel |
0.61 |
0.644 |
0.725** |
0.825** |
0.698 |
0.741* |
0.713 |
0.754* |
Liver, abs |
9.804 |
9.873 |
10.948* |
12.201** |
8.709 |
7.751** |
7.701** |
8.317 |
Liver, rel |
2.5 |
2.638 |
2.924** |
3.54** |
3.475 |
3.253 |
3.03** |
3.436 |
*p<=0.05 **p<=0.01
Abs=absolute rel=relative to final bodyweight
Applicant's summary and conclusion
- Conclusions:
- The NOAEC in this study was 1000 mg/m3 for male and female rats. The male kidney was identified as the target organ as increased hyaline casts and basophilic cortical tubules were observed in the kidneys of male animals exposed to 5000 mg/m3 onwards. These changes were associated with accumulation of alpha 2u globulin in cortical tubular cells. The presence of increased hyaline casts and basophilic cortical tubules are an indication of proximal tubular cell damage and a classical effect of α2µ-nephropathy which is male rat-specific effect not considered relevant human hazard assessment.
- Executive summary:
The 90-day inhalation exposure of rats to Isooctene at 1000, 5000 and 15000 mg/m3 induced toxicity in the male kidney (target organ), but no effects in the respiratory tract. Under the current test conditions, the no-observed adverse effect level (NOAEC) in this study is 1000 mg/m3 for the male and female rats.
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