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EC number: 203-726-8 | CAS number: 109-99-9
- 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
Genetic toxicity: in vivo
Administrative data
- Endpoint:
- in vivo mammalian somatic cell study: cytogenicity / erythrocyte micronucleus
- Remarks:
- Type of genotoxicity: chromosome aberration
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Study period:
- Start date Jan 11 1993
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- other: Generally comparable to a guideline study.
Cross-reference
- Reason / purpose for cross-reference:
- reference to same study
Data source
Reference
- Reference Type:
- study report
- Title:
- Unnamed
- Year:
- 1 998
- Report date:
- 1998
Materials and methods
Test guideline
- Qualifier:
- equivalent or similar to guideline
- Guideline:
- OECD Guideline 474 (Mammalian Erythrocyte Micronucleus Test)
- Principles of method if other than guideline:
- The study was conducted according to MacGregor et al. (Fundam. Appl. Toxicol Vol 114:513-522, 1990) and many of the experimental details provided in this endpoint summary are taken from that publication. The mice used in this study were taken from a repeated dose inhalation study reported in Section 7.5.3 of this file.
- GLP compliance:
- not specified
- Type of assay:
- micronucleus assay
Test material
- Reference substance name:
- Tetrahydrofuran
- EC Number:
- 203-726-8
- EC Name:
- Tetrahydrofuran
- Cas Number:
- 109-99-9
- Molecular formula:
- C4H8O
- IUPAC Name:
- tetrahydrofuran
- Details on test material:
- - Name of test material: tetrahydrofuran- Supplier: ChemCentral, Kansas City, MO, USA- Physical state: clear, colorless liquid- Analytical purity: approximately 99% (determined by elemental analysis)- Impurities: none identified greater than 0.1%- Purity test date: not provided- Lot/batch No.: lot WK8-6-86- Expiration date of the lot/batch: not provided- Stability under test conditions: stability studies indicated that tetrahydrofuran was stable as the bulk chemical for 2 weeks when stored protected from light at temperatures up to 25 deg C. Stability was monitored during the 14-week studies and no degradation of the bulk chemical was detected.- Storage condition of test material: at room temperature in the original metal containers under a nitrogen blanket- Other: Karl Fischer analysis indicated less than 0.06% water; peroxide concentrations were no greater than 3 ppm
Constituent 1
Test animals
- Species:
- mouse
- Strain:
- B6C3F1
- Sex:
- male/female
- Details on test animals or test system and environmental conditions:
- TEST ANIMALS- Source: Simonsen Laboratories, Inc., Gilroy, CA- Age at study initiation: 7 weeks (average)- Weight at study initiation: not available- Fasting period before study: No- Housing: Stainless-steel wire-bottom (Hazleton Systems, Inc., Aberdeen, MD), 1 animal/cage.- Diet: NIH-07 Open Formula Pelleted feed, ad libitum except during exposures- Water: Tap water (City of Richland municipal supply), ad libitum- Acclimation period: quarantined 15 days before the beginning of the studiesENVIRONMENTAL CONDITIONS (Exposure Chambers)- Temperature: 19.6 to 26.6 °C- Humidity (%): 29 to 75- Air changes (per hr): 15 +/- 3- Photoperiod (hrs dark / hrs light): 12/12IN-LIFE DATES: From: 12 February 1987 To: 15 May 1987
Administration / exposure
- Route of administration:
- inhalation: vapour
- Vehicle:
- Unchanged (no vehicle)
- Details on exposure:
- Vapor Generation/Exposure System:Tetrahydrofuran vapor was generated with a rotary evaporation system (Buchi Rotavapor, Model EL-131S, Buchi Laboratories Technik AG, Flavil, Switzerland). The vapor entered a short distribution manifold from which individual delivery lines carried metered amounts of the vapor to each exposure chamber. At equilibrium, each valve was opened to allow flow to chambers. At each chamber location, the vapor was injected into the chamber duct after dilution with an appropriate amount of charcoal- and HEPA-filtered chamber air to achieve the desired chamber concentration.The exposure system consisted of stainless-steel chambers designed at Batelle Northwest Laboratories (Hazelton 2000, Aberdeen, MD).
- Duration of treatment / exposure:
- 14 weeks
- Frequency of treatment:
- 6 hours plus T90 (12 minutes) per day, 5 days/week
- Post exposure period:
- None
Doses / concentrations
- Remarks:
- Doses / Concentrations:0 (chamber control), 66, 200, 600, 1800 and 5000 ppm Basis:nominal conc.
- No. of animals per sex per dose:
- 10
- Control animals:
- yes, concurrent no treatment
- Positive control(s):
- No
Examinations
- Tissues and cell types examined:
- Peripheral blood samples were obtained from male and female mice and smears immediately fixed. Slides were scanned at 630 or 1,000X magnification with a semiautomatic image analysis system to determine the frequency of micronuclei in 2,000 polychromatic erythrocytes (PCEs) and 10,000 normochromatic erythrocytes (NCEs) in up to 10 animals/exposure group.
- Details of tissue and slide preparation:
- CRITERIA FOR DOSE SELECTION: Animals dosed at 0 (chamber controls), 600, 1800 or 5000 ppm for 14 weeks in an inhalation toxicity test were chosen for this assay.TREATMENT AND SAMPLING TIMES:Immediately following the 14-week inhalation exposures, peripheral blood was obtained from male and female mice.DETAILS OF SLIDE PREPARATION:Peripheral blood was obtained from the ventral tail vessel. Smears from peripheral blood samples were immediately prepared and fixed in absolute methanol for about 2 minutes. Methanol-fixed slides were stained with Hoechst 33258/pyronin Y double fluorescent stain using Sorensen’s M/15 phosphate buffer.METHOD OF ANALYSIS: Slides were scored at 630X under oil-immersion microscopy. The incidence of micronucleated PCEs was scored for each animal. The polychromatic to normochromatic cell ratio was based on the number of PCEs noted in the first 100 normochomatic erythrocytes (NCEs). If no PCEs were seen in the first 100 NCEs, an automated system for counting 10,000 cells was employed and the slide was not scored if the ratio was less than 0.5%.
- Evaluation criteria:
- An individual trial was considered positive if the trend test P value was = to 0.025 or if the P value for any single exposure group was = 0.025 divided by the number of exposure groups. A final call of positive for the micronucleus test was preferably based on reproducibly positive trials. The final call concerning a positive or negative finding was determined by the scientific staff after considering the results of statistical analysis, the reproducibility of any effects observed, and the magnitude of those effects.
- Statistics:
- The results were tabulated as the mean of the pooled results from all animals within a treatment group plus or minus the standard error of the mean. The frequency of micronucleated cells among NCEs and PCEs were analyzed by a statistical software package that tested for increasing trend over exposure groups with a one-tailed Cochran-Armitage trend test, followed by pairwise comparisons between each exposed group and the control.
Results and discussion
Test resultsopen allclose all
- Sex:
- male
- Genotoxicity:
- negative
- Remarks:
- micronucleated cells/1000 PCE cells
- Vehicle controls validity:
- valid
- Sex:
- male
- Genotoxicity:
- ambiguous
- Remarks:
- micronucleated cells/1000 NCE cells, trend test P = 0.074
- Vehicle controls validity:
- valid
- Sex:
- female
- Genotoxicity:
- negative
- Remarks:
- micronucleated cells/1000 PCE cells
- Vehicle controls validity:
- valid
- Sex:
- female
- Genotoxicity:
- negative
- Remarks:
- micronucleated cells/1000 NCE cells
- Vehicle controls validity:
- valid
Any other information on results incl. tables
The frequency of micronuclei in mouse peripheral blood erythrocytes following treatment with tetrahydrofuran by inhalation for 14 weeks is presented in the following table.
Micronucleated Cells/1000 Cells | |||||
Treatment | Dose (ppm) | Number of Mice Scored | PCEs | NCEs | Significance |
Male | |||||
Chamber control | 10 | 1.50 +/- 0.29 | 1.18 +/- 0.09 | ||
Tetrahydrofuran | 600 | 10 | 1.69 +/- 0.25 | 1.27 +/- 0.10 | |
1800 | 10 | 1.79 +/- 0.22 | 1.58 +/- 0.08* | ||
5000 | 7 | 1.47 +/- 0.27 | 1.41 +/- 0.13 | P = 0.297 (PCEs) P = 0.074 (NCEs) | |
Female | 10 | 1.85 +/- 0.38 | 1.43 +/- 0.18 | ||
Chamber control | 600 | 10 | 1.01 +/- 0.24 | 1.16 +/- 0.07 | |
Tetrahydrofuran | 1800 | 10 | 1.34 +/- 0.31 | 1.15 +/- 0.07 | |
5000 | 10 | 1.29 +/- 0.19 | 1.18 +/- 0.08 | P = 0.297 (PCEs) P = 0.074 (NCEs) |
* Significantly different from control (P=0.004)
Significance tested by the one-tailed trend test; P < 0.025
Applicant's summary and conclusion
- Conclusions:
- Interpretation of results (migrated information): negativeIn female mice, the frequencies of micronucleated cells in polychrmatic or normochromatic erythrocytes were not increased. In male mice, a small increase in the frequency of micronucleated normochromatic erythrocytes was concluded to represent an equivocal response. No significant increase was seen in polychromatic erythrocytes.
- Executive summary:
The frequencies of micronucleated erythorcytes were determined in peripheral blood samples obtained from male and female mice dosed by inhalation at 0 (chamber control), 600, 1800 or 5000 ppm in 14 -week inhalation toxicity studies. With the exception of an equivocal response in male mice represented as an increased frequency of micronucleated normochromatic cells (P = 0.074), tetrahydrofuran failed to produce a positive response in female mice based on micronucleated polychromatic or normochromatic erythrocytes or a positive response in male mice based on micronucleated polychromatic erythrocytes.
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