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Diss Factsheets
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EC number: 926-605-8 | CAS number: -
- 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
![](https://echa.europa.eu/o/diss-blank-theme/images/factsheets/A-REACH/factsheet/print_toxicological-information.png)
Developmental toxicity / teratogenicity
Administrative data
- Endpoint:
- developmental toxicity
- Type of information:
- migrated information: read-across based on grouping of substances (category approach)
- Adequacy of study:
- key study
- Study period:
- 198903-27 to 1989-04-20
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- other: This study is classified as reliable without restrictions because it is well documented and follows OECD Guideline 414.
Data source
Reference
- Reference Type:
- study report
- Title:
- Unnamed
- Year:
- 1 989
- Report date:
- 1989
Materials and methods
Test guideline
- Qualifier:
- equivalent or similar to guideline
- Guideline:
- OECD Guideline 414 (Prenatal Developmental Toxicity Study)
- GLP compliance:
- yes (incl. QA statement)
Test material
- Details on test material:
- - Name of test material (as cited in study report): commercial hexane
- Composition of test material, percentage of components: 52.19% n-hexane
Constituent 1
Test animals
- Species:
- mouse
- Strain:
- CD-1
- Details on test animals or test system and environmental conditions:
- TEST ANIMALS
- Source: Charles River Breeding Laboratories, Kingston, NY
- Age at study initiation: 42 days at arrival
- Weight at study initiation: 30 g male, 24 g females
- Housing: individually in stainless steel wire mesh cages, identified with toe clips and ear notches
- Diet (e.g. ad libitum): Prolab Certified Rodent Food, ad libitum
- Water (e.g. ad libitum): tap water, ad libitum
- Acclimation period: 2 weeks
ENVIRONMENTAL CONDITIONS
- Temperature (°C): 66-72 degree F
- Humidity (%): 50-71
- Photoperiod (hrs dark / hrs light): 12 hrs light/12 hrs dark
IN-LIFE DATES: From: April 5, 1989 To: April 18, 1989
Administration / exposure
- Route of administration:
- inhalation: vapour
- Type of inhalation exposure (if applicable):
- whole body
- Details on exposure:
- GENERATION OF TEST ATMOSPHERE / CHAMBER DESCRIPTION
- Exposure apparatus: 4320 l glass and stainless steel chambers.
- Method of holding animals in test chamber: cages
- Source and rate of air: 1000 l/min
- Method of conditioning air: Test substance was metered from a piston pump into one or two heated glass evaporator with a temperature of 27-70 degree C. Conditioned air was passed through the evaporator, where it carried the vapor into the exposure chamber.
- Temperature, humidity: monitored every 30 minutes
- Air flow rate: 1000 l/min
- Air change rate: 20 min, 14 air changes per hour
- Treatment of exhaust air: filtration
TEST ATMOSPHERE
- Brief description of analytical method used: GC with flame ionization detection
- Samples taken from breathing zone: yes, 7 times per exposure - Analytical verification of doses or concentrations:
- yes
- Details on analytical verification of doses or concentrations:
- Samples were taken seven times per exposure period and analyzed with GC-FID. Distribution of test substance was evaluated by sampling five different areas of the exposure chamber.
- Details on mating procedure:
- - Impregnation procedure: cohoused
- If cohoused:
- M/F ratio per cage: 1/1
- Length of cohabitation: March 27, 1989-April 2, 1989
- Proof of pregnancy: vaginal plug referred to as day 0 - Duration of treatment / exposure:
- gestation day (GD) 6-15
- Frequency of treatment:
- 6 hrs/day
- Duration of test:
- GD 18
Doses / concentrationsopen allclose all
- Remarks:
- Doses / Concentrations:
0, 900, 3000, 9000 ppm
Basis:
nominal conc.
- Remarks:
- Doses / Concentrations:
914, 3026, 9107 ppm
Basis:
analytical conc.
- No. of animals per sex per dose:
- 30 pregnant females per exposure group
- Control animals:
- yes
Examinations
- Maternal examinations:
- CAGE SIDE OBSERVATIONS: Yes
- Time schedule: daily
- Cage side observations: mortality, clinical signs
BODY WEIGHT: Yes
- Time schedule for examinations: GD 0, 6, 9, 12, 15
FOOD CONSUMPTION: Yes
WATER CONSUMPTION: Yes
POST-MORTEM EXAMINATIONS: Yes
- Sacrifice on gestation day # 18
- Organs examined: gravid uterus, ovaries, cervix, vagina, abdominal cavities, thoracic cavities, liver, kidneys
- Ovaries and uterine content:
- The ovaries and uterine content was examined after termination: Yes
Examinations included:
- Number of corpora lutea: Yes
- Number of early resorptions: Yes
- Number of late resorptions: Yes
- Other: live and dead fetuses - Fetal examinations:
- - External examinations: Yes: all per litter
- Soft tissue examinations: Yes: half per litter were examined for thoracic and abdominal visceral abnormalities
- Skeletal examinations: Yes: half per litter
- Head examinations: Yes: [all per litter / half per litter / #? per litter ] / No / No data - Statistics:
- Quantitative continuous variables were compared by use of Levene's test for equal variance, analysis of variance, and t-tests with Bonferroni probabilities. Nonparametric data was evaluated using the Kruskal-Wallis test, followed by the Mann-Whitney U test. Indices were compared using Fisher's exact test. 0.05 was used as the criteria for statistical significance.
Results and discussion
Results: maternal animals
Maternal developmental toxicity
- Details on maternal toxic effects:
- Maternal toxic effects:yes
Details on maternal toxic effects:
There were no significant treatment related effects to body weight, clinical signs, food consumption, weight changes, or organ weights. There was increased water consumption on GD 6-9, 9-12, 6-15, and 15-18 in the 3000 ppm group. There was also increased water consumption in the 900 ppm group on GD 3-6 and 6-9. There was a statistically significant increase in lung color changes in the 9000 ppm group. Four dams also had brown foci. Two dams in the 3000 ppm group had lung color changes as well, and three had dark brown foci.
Effect levels (maternal animals)
open allclose all
- Dose descriptor:
- NOAEC
- Effect level:
- 900 ppm
- Based on:
- test mat.
- Basis for effect level:
- other: maternal toxicity
- Dose descriptor:
- LOAEC
- Effect level:
- 3 000 ppm
- Based on:
- test mat.
- Basis for effect level:
- gross pathology
Results (fetuses)
- Details on embryotoxic / teratogenic effects:
- Embryotoxic / teratogenic effects:yes
Details on embryotoxic / teratogenic effects:
Gestational parameters were similar between exposure and control groups. There was a statistically significant increase in two skeletal malformations in the 9000 ppm group, bilateral bone island at the first lumbar arch, all intermediate phalanges of the hindlimb unossified. No other dose related abnormalities were noted.
Effect levels (fetuses)
open allclose all
- Dose descriptor:
- NOAEC
- Effect level:
- 3 000 ppm
- Based on:
- test mat.
- Sex:
- not specified
- Basis for effect level:
- skeletal malformations
- Dose descriptor:
- LOAEC
- Effect level:
- 9 000 ppm
- Based on:
- test mat.
- Sex:
- not specified
- Basis for effect level:
- skeletal malformations
Fetal abnormalities
- Abnormalities:
- not specified
Overall developmental toxicity
- Developmental effects observed:
- not specified
Any other information on results incl. tables
Results of Developmental Toxicity Study on Mice
0.0 ppm |
900.0 ppm |
3000.0 ppm |
9000.0 ppm |
|
No. of dams with lung color change |
0 |
0 |
2 |
12 |
All inter. Phalanges (hindlimb) unossified (litters, %) |
76.9 |
72.0 |
84.0 |
100.0 |
Bone island - first lumbar arch - bilateral (litters, %) |
0.0 |
0.0 |
8.0 |
23.1 |
Applicant's summary and conclusion
- Conclusions:
- In mice, the maternal NOAEC was 900 ppm, and the maternal LOAEC was 3000 ppm (10560 mg/m3) based on color changes in the lungs. The developmental NOAEC was 3000 ppm and the LOAEC was 9000 ppm(31680 mg/m3) in mice.
- Executive summary:
The purpose of this study was to examine the developmental toxicity of commercial hexane in mice. Groups of 30 pregnant female mice were exposed to concentrations of 0, 900, 3000, or 9000 ppm for 6 hrs/day during gestational days 6 -15. The animals were then sacrificed on GD 18. During the study, the animals were examined for clinical signs, mortality, food and water consumption, and body weights taken. After sacrifice, the internal organs were examined, and the uterus was examined for viable fetuses, number of resorptions, and number of corpora lutea. Fetuses were examined for malformations. Necropsy revealed color changes in the lungs of females in the 3000 and 9000 ppm groups. Fetuses in from dams in the 9000 ppm group had a statistically significant increase in some skeletal abnormalities. The maternal NOAEC in mice was 900 ppm (3168 mg/m3), and the LOAEC 3000 ppm based on lung color changes. The developmental NOAEC in mice was 3000 ppm (10560 mg/m3) and the LOAEC 9000 ppm (31680 mg/m3) based on skeletal abnormalities.
Information on Registered Substances comes from registration dossiers which have been assigned a registration number. The assignment of a registration number does however not guarantee that the information in the dossier is correct or that the dossier is compliant with Regulation (EC) No 1907/2006 (the REACH Regulation). This information has not been reviewed or verified by the Agency or any other authority. The content is subject to change without prior notice.
Reproduction or further distribution of this information may be subject to copyright protection. Use of the information without obtaining the permission from the owner(s) of the respective information might violate the rights of the owner.
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