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EC number: 700-263-8 | CAS number: 89686-69-1
- 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:
- short-term repeated dose toxicity: oral
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Study period:
- 13 June - 3 September, 2007
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- guideline study
Data source
Reference
- Reference Type:
- study report
- Title:
- Unnamed
- Year:
- 2 008
- Report date:
- 2008
Materials and methods
Test guidelineopen allclose all
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 407 (Repeated Dose 28-Day Oral Toxicity Study in Rodents)
- Deviations:
- no
- Qualifier:
- according to guideline
- Guideline:
- EU Method B.7 (Repeated Dose (28 Days) Toxicity (Oral))
- Deviations:
- no
- Qualifier:
- according to guideline
- Guideline:
- other: EPA OPPTS 870.3050 (28-Day Oral Toxicity in Rodents)
- Deviations:
- no
- GLP compliance:
- yes (incl. QA statement)
- Limit test:
- no
Test material
- Reference substance name:
- 2-[2-(oxolan-2-yl)propan-2-yl]oxolane
- EC Number:
- 700-263-8
- Cas Number:
- 89686-69-1
- Molecular formula:
- C11 H20 O2
- IUPAC Name:
- 2-[2-(oxolan-2-yl)propan-2-yl]oxolane
- Test material form:
- liquid
- Details on test material:
- - Name of test material (as cited in study report): Ditetrahydrofurylpropane
- Lot/batch No.: 6-7B09
- Analytical purity: 99.7%
- Substance type: Clear colourless liquid
- Physical state: liquid
- Purity test date: 09 February 2007
- Expiration date of the lot/batch: 09 February 2010
- Storage condition of test material: At room temperature in the dark
- Stability under storage conditions: Stable
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 Deutschland, Sulzfeld, Germany.
- Age at study initiation: Approximately 6 weeks.
- Weight at study initiation: Males 169-212 g; Females 147-176 g
- Fasting period before study: Not applicable
- Housing: Group housing of 5 animals per sex in Macrolon cages (MIV type; during overnight activity monitoring individual housing in MIII type) with sterilised sawdust as bedding material and paper as cage-enrichment. No cage-enrichment was provided during overnight activity monitoring.
- Diet (e.g. ad libitum): ad libitum
- Water (e.g. ad libitum): ad libitum
- Acclimation period: at least 5 days before start of treatment under laboratory conditions.
ENVIRONMENTAL CONDITIONS
- Temperature (°C): 20.7 – 23.7°C
- Humidity (%): 42 - 83%; Cleaning procedures in the room might have caused the temporary fluctuations above the optimal maximum level of 70% for relative humidity. Based on laboratory historical data, these fluctuations were considered not to have affected the study integrity.
- Air changes (per hr): 15
- Photoperiod (hrs dark / hrs light): 12/12; Temporary fluctuations from the light/dark cycle (with a maximum of 1 hour) occurred due to performance of functional observations in the room. Based on laboratory historical data, these fluctuations were considered not to have affected the study integrity.
Administration / exposure
- Route of administration:
- oral: gavage
- Vehicle:
- water
- Details on oral exposure:
- PREPARATION OF DOSING SOLUTIONS:
The test substance was dosed undiluted at 150 and 500 mg/kg/day. To allow accurate dosing at 50 mg/kg/day in undiluted form, water was used as vehicle for this dose group. Formulations (w/w) were prepared daily within 5 hours prior to dosing, and were homogenised to visually acceptable levels. No correction was made for the purity of the test substance.
VEHICLE
- Concentration in vehicle: 5 mg/ml
- Amount of vehicle (if gavage): 10 ml/kg - Analytical verification of doses or concentrations:
- yes
- Details on analytical verification of doses or concentrations:
- Samples of group 1 (0 mg/kg bw/d) and 2 (50 mg/kg bw/d) prepared for use on Day 12 were analysed to check homogeneity (group 2 only) and accuracy of preparation. The analytical method used (GC-FID) can be found in section 8 of this IUCLID file.
Test substance formulations in water (i.e. Group 2) formed a homogeneous suspension. For the formulation of Group 2, the concentrations analysed for some samples were below the target concentrations (79% to 87% of target). For all other samples from Group 2, the concentrations analysed were in agreement with target concentrations (91% to 94% of target).
Since the GC method developed proved to be prone to variation due to the great number of water injections made, the obtained results were the best achievable and, thus, were accepted. - Duration of treatment / exposure:
- At least 28 days.
- Frequency of treatment:
- Once daily, 7 days per week, approximately the same time each day with a maximum of 5 hours difference between the earliest and latest dose.
Doses / concentrationsopen allclose all
- Dose / conc.:
- 50 mg/kg bw/day (actual dose received)
- Dose / conc.:
- 150 mg/kg bw/day (actual dose received)
- Dose / conc.:
- 500 mg/kg bw/day (actual dose received)
- No. of animals per sex per dose:
- 5
- Control animals:
- yes, concurrent vehicle
- Details on study design:
- - Dose selection rationale: Dose levels are based on results of an 8-day dose range finding study with Ditetrahydrofurylpropane
Animals at 150 mg/kg/day (Group 3) were inadvertently dosed on day 7 with a dose volume being significantly higher than intended (i.e. approximately 5 ml/kg instead of 0.15 ml/kg). It was evaluated that this adversely affected the study integrity, due to mortality/moribundity that subsequently occurred in this group. Therefore, a new group of animals (Group 5) was added to the study to restore the study integrity. These animals were treated at the same dose level as the initial Group 3 animals for 28 days, and the results of Group 5 replaced the results of Group 3.
Examinations
- Observations and examinations performed and frequency:
- CAGE SIDE OBSERVATIONS: Yes
- Time schedule: At least twice daily.
- Cage side observations included: Mortality / Viability
DETAILED CLINICAL OBSERVATIONS: Yes
- Time schedule: At least once daily
BODY WEIGHT: Yes
- Time schedule for examinations: weekly
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: Yes, weekly
HAEMATOLOGY: Yes
- Time schedule for collection of blood: immediately prior to scheduled post mortem examination
- Anaesthetic used for blood collection: Yes (iso-flurane )
- Animals fasted: Yes, overnight (with a maximum of 20 hours)
- How many animals: all surviving animals
- Parameters examined: White blood cells, Differential leucocyte count (neutrophils, lymphocytes, monocytes, eosinophils, basophils), Red blood cells, Reticulocytes, Red blood cell distribution width, Haemoglobin, Haematocrit, Mean corpuscular volume, Mean corpuscular haemoglobin, Mean corpuscular haemoglobin concentration, Platelets, Prothrombin time, Activated Partial thromboplastin time
CLINICAL CHEMISTRY: Yes
- Time schedule for collection of blood: immediately prior to scheduled post mortem examination
- Animals fasted: Yes, overnight (with a maximum of 20 hours)
- How many animals: all surviving animals
- Parameters examined: Alanine aminotransferase, Aspartate aminotransferase, Alkaline phosphatase, Total Protein, Albumin, Total Bilirubin, Urea, Creatinine, Glucose, Cholesterol, Sodium, Potassium, Chloride, Calcium, Inorganic Phosphate
NEUROBEHAVIOURAL EXAMINATION: Yes
- Time schedule for examinations: During week 4 of treatment
- Dose groups that were examined: all
- Battery of functions tested: hearing ability, pupillary reflex, static righting reflex and grip strength, motor activity test - Sacrifice and pathology:
- GROSS PATHOLOGY: Yes, Samples of the following tissues and organs were collected from all animals at necropsy and fixed in 10% buffered formalin Identification marks: not processed, Adrenal glands, Aorta, Brain [cerebellum, mid-brain, cortex], Caecum, Cervix, (Clitoral gland), Colon, Duodenum, Epididymides, Eyes with optic nerve [if detectable], (Harderian gland), (Female mammary gland area), (Femur including joint), Heart, Ileum, Jejunum, Kidneys, (Larynx), (Lacrimal gland, exorbital), Liver, Lung infused with formalin, Lymph nodes - mandibular, mesenteric, (Nasopharynx), Oesophagus, Ovaries, Pancreas, Peyer's patches [jejunum, ileum] if detectable, Pituitary gland, (Preputial gland), Prostate gland, Rectum, (Salivary glands - mandibular, sublingual), Sciatic nerve, Seminal vesicles, (Skeletal muscle), (Skin), Spinal cord -cervical/midthoracic/lumbar, Spleen, Sternum with bone marrow, Stomach, Testes, Thymus, Thyroid including parathyroid [if detectable], (Tongue), Trachea, Urinary bladder, Uterus, Vagina, All gross lesions
Tissues/organs mentioned in parentheses were not examined by the pathologist, since no signs of toxicity were noted at macroscopic examination.
ORGAN WEIGHTS: Yes, recorded from the surviving animals on the scheduled day of necropsy:
Adrenal glands, Brain, Epididymides, Heart, Kidneys, Liver, Spleen, Testes, Thymus
HISTOPATHOLOGY: Yes
- all tissues collected at the scheduled sacrifice from all group 1 and 4 animals,
- all tissues from all animals of all dose groups which died spontaneously or were terminated in extremis,
- all gross lesions.
Based on (possible) treatment-related changes in the liver and kidneys the histological examination was extended to those particular organs of all animals of groups 2 and 5 (males and/or females). All abnormalities were described and included in the report. An attempt was made to correlate gross observations with microscopic findings. - Statistics:
- The following statistical methods were used to analyse the data:
- If the variables could be assumed to follow a normal distribution, the Dunnett-test1 (many-to-one t-test) based on a pooled variance estimate was applied for the comparison of the treated groups and the control groups for each sex.
- The Steel-test2 (many-to-one rank test) was applied when the data could not be assumed to follow a normal distribution.
- The exact Fisher-test3 was applied to frequency data.
All tests were two-sided and in all cases p < 0.05 was accepted as the lowest level of significance. Group means were calculated for continuous data and medians were calculated for discrete data (scores) in the summary tables. Test statistics were calculated on the basis of exact values for means and pooled variances.
Results and discussion
Results of examinations
- Clinical signs:
- effects observed, treatment-related
- Description (incidence and severity):
- Lethargy, flat posture, uncoordinated movements, abnormal gait and/or ptosis were noted among animals treated at 500 mg/kg/day between days 1 and 3.
There were no clinical signs of toxicity noted in animals at 0, 50 and 150 mg/kg/day during the observation period.
Salivation observed in animals of the 150 and 500 mg/kg/day dose groups was considered to be a physiological response to the taste of the test substance rather than a sign of systemic toxicity, considering the nature and minor severity of the effect and its time of occurence (i.e. after dosing). Alopecia and scabs are commonly noted in rats of this age and strain which are housed and treated under the conditions in this study. At the incidence observed, these were considered signs of no toxicological significance. - Mortality:
- no mortality observed
- Description (incidence):
- The death of one male (no.10), at 50 mg/kg/day was considered to be due to a gavage accident (i.e. based on fluid noted in the thoracic cavity and microscopic abnormalities). No further mortality occurred during the study period.
- Body weight and weight changes:
- no effects observed
- Description (incidence and severity):
- Body weights and body weight gain of treated animals were considered to have been unaffected by treatment with the test substance.
The higher body weight gain of animals at 150 mg/kg/day (achieving a level of statistical significance for females) was considered to be due to the fact that these animals were not of the same delivery as group 1, 2 and 4 animals, as they were added to the study to replace the initial group 3 animals. Means were also within the normal range for rats of this age and strain. Therefore, these changes were considered not related to treatment with the test substance. No toxicological significance was ascribed to the slightly higher body weight gain (statistically significant) of females at 50 and 500 mg/kg/day in the first week of the study, as these changes were of a temporary and mild nature. Body weight gain of these females during the study remained well within normal limits for female rats of this age and strain. - Food consumption and compound intake (if feeding study):
- no effects observed
- Description (incidence and severity):
- Food consumption before or after allowance for body weight was similar between treated and control animals.
Relative food intake of females at 500 mg/kg/day was slightly reduced during the first two weeks of treatment. Since this change was of a temporary nature, it was considered to be of no toxicological relevance. - Food efficiency:
- not examined
- Water consumption and compound intake (if drinking water study):
- not examined
- Ophthalmological findings:
- not examined
- Haematological findings:
- no effects observed
- Description (incidence and severity):
- No toxicologically relevant changes occurred in haematological parameters of treated rats.
Any statistically significant changes at 150 mg/kg/day were considered to be of no toxicological significance as the changes occurred in the absence of a treatment-related distribution and/or remained within the range considered normal for rats of this age and strain. These changes included increased haemoglobin levels in males, increased mean corpuscular haemoglobin (MCH) and mean corpuscular haemoglobin concentration (MCHC) in males and females and reduced relative monocyte counts in males and females (not statistically significant for females).
The minor statistically significant reduction in prothrombin time (PT) in females at 500 mg/kg/day was considered not to represent a change of toxicological significance, because the mean remained well within the range considered normal for rats of this age and strain. - Clinical biochemistry findings:
- effects observed, treatment-related
- Description (incidence and severity):
- The following (statistically significant) changes in clinical biochemistry parameters distinguished treated animals from control animals:
- Reduced aspartate aminotransferase (ASAT) levels in females at 500 mg/kg/day,
- Increased alanine aminotransferase activity (ALAT) in one male (no. 19) at 500 mg/kg/day,
- Increased total protein levels in females at 150 and 500 mg/kg/day,
- Increased albumin levels in females at 150 and 500 mg/kg/day,
- Reduced total bilirubin levels in males at 150 and 500 mg/kg/day,
- Reduced glucose levels in males at 500 mg/kg/day and increased glucose level in one female (no. 38) at 500 mg/kg/day,
- Increased cholesterol level in one female at 500 mg/kg/day (no. 38),
- Increased potassium level in one female at 500 mg/kg/day (no. 38),
- Increased calcium levels in females at 150 and 500 mg/kg/day (not statistically significant at 150 mg/kg/day),
- Increased inorganic phosphate levels in males at 500 mg/kg/day, and in one female (no. 38) at 500 mg/kg/day.
No toxicological significance was ascribed to the slight but statistically significant higher calcium level in males at 150 mg/kg/day. This change occurred in the absence of a dose-related distribution and the mean value remained within the range considered normal for rats of this age and strain. - Urinalysis findings:
- not examined
- Behaviour (functional findings):
- no effects observed
- Organ weight findings including organ / body weight ratios:
- effects observed, treatment-related
- Description (incidence and severity):
- Increased liver weights (not statistically significant in males) and liver to body weight ratios were observed in males at 500 mg/kg/day and in females at 150 and 500 mg/kg/day. The increase in liver weight was more pronounced in females than in males, i.e. approximately 20 and 43% for males and females respectively (corrected for body weight). In addition, increased kidney weights and kidney to body weight ratios were observed in males at 500 mg/kg/day.
No toxicological significance was ascribed to the increased kidney weight and kidney to body weight ratio in females at 150 mg/kg/day. This change occurred in the absence of a dose-related distribution and mean values remained within the range considered normal for rats of this age and strain. - Gross pathological findings:
- no effects observed
- Description (incidence and severity):
- An accentuated lobular pattern of the liver was observed in one male (no. 19) at 500 mg/kg/day.
In the male at 50 mg/kg/day that died spontaneously on day 2, watery-clear fluid and many yellowish nodules grown together with the lungs were observed in the thoracic cavity. These findings indicate a gavage accident and were considered not related to the test substance. Other findings in this animal consisted of a reduced size of epididymides and seminal vesicles, and enlargement of the thymus. Incidental findings among other control and treated animals included enlargement of the mandibular lymph nodes, a sore in the throat region of the skin, reddish foci on the lungs, gray-white foci on the adrenals, fluid in the uterus and a watery-clear cyst in the right horn of the uterus. These findings are occasionally seen among rats used in these types of studies. In the absence of a dose-related distribution they were considered changes of no toxicological significance. - Histopathological findings: non-neoplastic:
- effects observed, treatment-related
- Description (incidence and severity):
- The following treatment related microscopic findings were noted:
- Midzonal/centrilobular hypertrophy (minimal or slight degree) in the liver of 4/5 males and 4/5 females at 500 mg/kg bw/day.
- Increased incidence and severity of cortical hyaline droplets in males at 150 mg/kg bw/day (slight degree) and males at 500 mg/kg bw/day (moderate degree).
- Increased incidence of slight or moderate degrees of corticomedullary tubular basophilia in 2/5 males at 150 mg/kg bw/day and 4/5 males at 500 mg/kg bw/day.
All other microscopic findings were within the range of background pathology encountered in Wistar rats of this age and strain and occurred at similar incidences and severity in both control and treated rats. - Histopathological findings: neoplastic:
- not examined
Effect levels
- Key result
- Dose descriptor:
- NOAEL
- Effect level:
- 50 mg/kg bw/day (actual dose received)
- Based on:
- test mat.
- Sex:
- male/female
- Basis for effect level:
- other: Based on effects on liver and kidneys in animals at 150 mg/kg/day and higher.
Target system / organ toxicity
- Critical effects observed:
- not specified
Applicant's summary and conclusion
- Conclusions:
- Based on a repeated dose toxicity study performed according to OECD/EC guidelines and GLP principes, a No Observed Adverse Effect Level (NOAEL) for Ditetrahydrofurylpropane of 50 mg/kg/day was established, based on effects on liver and kidneys in animals at 150 mg/kg bw/day and higher.
- Executive summary:
Wistar rats were treated with Ditetrahydrofurylpropane for 28 consecutive days by daily oral gavage at dose levels up to 500 mg/kg/day.
No signs of toxicity were noted during the in-life phase, except for the first few days during which lethargy, flat posture, uncoordinated movements, abnormal gait and/or ptosis were noted among animals treated at 500 mg/kg/day.
Increased liver weights were noted at necropsy in males at 500 mg/kg/day and females at 150 and 500 mg/kg/day, along with a single occasion of an accentuated lobular pattern of the liver in one of these males. At 500 mg/kg/day, this was supported by midzonal/centrilobular hypertrophy of the liver in both sexes. The location of the hypertrophy in centrilobular and midzonal hepatocytes and absence of any morphological lesions indicative of hepatocytotoxicity was consistent with that of an adaptive change. The lower total bilirubin levels and aspartate aminotransferase activity at 500 mg/kg/day could reflect adaptive changes in the liver. However, considering the magnitude of the increase in liver weight in these animals (i.e. approximately 20 and 43% for males and females respectively), the increased liver weight was considered to be of an adverse nature. In addition, a number of clinical biochemistry parameters were observed that suggest an effect of the test substance on liver function. These parameters included increased total protein, albumin, glucose and cholesterol levels in (individual) females at 150 and 500 mg/kg/day and reduced glucose levels in males at 500 mg/kg/day.
In the kidneys of male rats at 150 and 500 mg/kg/day, an increase in the incidence and severity of cortical hyaline droplets was observed. These droplets were considered to represent alpha-2u-globulin, a normal protein in male rats that undergoes reabsorption in the proximal cortical tubules. A range of chemicals are known to increase hyaline droplet formation beyond the physiological capacity of the tubular epithelium which may then result in tubular epithelial cell damage (hyaline droplet nephropathy) which was evident in this study as an increase in the severity of corticomedullary tubular basophilia in males at 150 and 500 mg/kg/day. Kidney weights were also increased at these dose levels. An increase in the incidence/severity of cortical hyaline droplets is a specific male rat response which is not observed in normal female rats and higher species of either sex, including humans.
Other changes in clinical biochemistry parameters included increased calcium levels in females at 150 and 500 mg/kg/day, increased inorganic phosphate levels in males at 500 mg/kg/day, and an increased inorganic phosphate and potassium level in one female at 500 mg/kg/day.
The increase in calcium levels in females at 150 and 500 mg/kg/day coincides with an increase in albumin levels in these animals. As albumin is a major calcium binding protein and no correlating morphological changes of these animals were observed, this change probably reflects the increase in albumin levels and is considered of no toxicological significance.
From the results presented in this report, a definitive No Observed Adverse Effect Level (NOAEL) for Ditetrahydrofurylpropane of 50 mg/kg/day was established, based on effects on liver and kidneys in animals at 150 mg/kg/day and higher.
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