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EC number: 701-198-8 | 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
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:
- 1995
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- other: According to or similar to guideline study OECD 422: GLP
- Justification for type of information:
- A discussion and report on the read across strategy is given as an attachment in IUCLID Section 13.
Cross-referenceopen allclose all
- Reason / purpose for cross-reference:
- read-across: supporting information
Reference
- Endpoint:
- short-term repeated dose toxicity: oral
- Type of information:
- read-across based on grouping of substances (category approach)
- Adequacy of study:
- key study
- Study period:
- 1995
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- other: According to or similar to guideline study OECD 422: GLP
- Justification for type of information:
- A discussion and report on the read across strategy is given as an attachment in IUCLID Section 13.
- Reason / purpose for cross-reference:
- read-across source
- Reason / purpose for cross-reference:
- reference to same study
- Qualifier:
- equivalent or similar to guideline
- Guideline:
- OECD Guideline 422 (Combined Repeated Dose Toxicity Study with the Reproduction / Developmental Toxicity Screening Test)
- GLP compliance:
- yes
- Limit test:
- yes
- Species:
- rat
- Strain:
- Sprague-Dawley
- Sex:
- male/female
- Route of administration:
- oral: gavage
- Vehicle:
- not specified
- Details on oral exposure:
- Males were treated from day 14 prior to the mating phase until the end of the mating phase and then killed, Females were treated from day 14 prior to mating, through day 4 of lactation and then killed.
- Analytical verification of doses or concentrations:
- not specified
- Duration of treatment / exposure:
- Males were treated from day 14 prior to the mating phase until the end of the mating phase and then killed, Females were treated from day 14 prior to mating, through day 4 of lactation and then killed.
- Frequency of treatment:
- 7days/week
- Remarks:
- Doses / Concentrations:
0, 25, 150, or 1000 mg/kg/day (10 ml/kg dosing volume)
Basis:
other: gavage - No. of animals per sex per dose:
- 10 male, 10 female per group
Control group: 10 male, 10 female, 0.5% methylcellulose - Control animals:
- yes
- Observations and examinations performed and frequency:
- Effects on general toxicity, neurobehavioral activity, clinical chemistry, and hematology were evaluated. Gross necropsies and histopathologic examination of tissues were conducted with emphasis on the male reproductive tract.
- Sacrifice and pathology:
- All surviving animals were sacrificed following dosing
- Statistics:
- Adult body and organ weight, food consumption, clinical chemistry, open field activity and hematologic data (raw or transformed) were compared using either parametric or nonparametric (Kruskal-Wallis) ANOVA depending on whether the data were found to be homogeneous or nonhomogeneous using Bartlett's homogeneity of variance procedure. If ANOVA analysis indicated significant differences, Dunnett's test and Mann Whitney's U test, for parametric and nonparemetric data, respectively, were used to analyze for differences between the various dose groups.
- Clinical signs:
- no effects observed
- Mortality:
- no mortality observed
- Body weight and weight changes:
- no effects observed
- Food consumption and compound intake (if feeding study):
- no effects observed
- Food efficiency:
- not specified
- Water consumption and compound intake (if drinking water study):
- not examined
- Ophthalmological findings:
- not examined
- Haematological findings:
- no effects observed
- Clinical biochemistry findings:
- no effects observed
- Urinalysis findings:
- no effects observed
- Behaviour (functional findings):
- no effects observed
- Organ weight findings including organ / body weight ratios:
- no effects observed
- Gross pathological findings:
- no effects observed
- Histopathological findings: non-neoplastic:
- no effects observed
- Histopathological findings: neoplastic:
- no effects observed
- Details on results:
- No deaths or clinical signs of toxicity or behavioral changes were noted. No significant differences in body weights or feed consumption were observed. Startle reflex, open field test, and forelimb grip reflex performance data also revealed no treatment-related findings.
There were also no treatment-related changes in hematology or blood chemistry parameters, organ weights or gross pathology. An apparent treatment-related, slight to moderate hyperplasia of the non-glandular mucosa of the stomach, associated with degeneration, hyperkeratosis and submucosal subacute inflammation and, in a few cases, with erosion, was seen in animals of all treated groups. This effect was considered an artifact of the dosing method and not directly related to the toxicity of the test material. No other treatment related histological changes were observed. - Dose descriptor:
- NOAEL
- Effect level:
- >= 1 000 mg/kg bw/day (nominal)
- Sex:
- male/female
- Basis for effect level:
- other: No treatment-related mortality or significant adverse clinical effects occurred.
- Critical effects observed:
- not specified
- Conclusions:
- Based on these data, the no-observable- adverse effect level (NOAEL) for repeated dose toxicty was >= 1000 mg/kg/day, the highest dose tested.
- Executive summary:
Groups of 10 male and 10 female Sprague Dawley rats were dosed with decane daily by gavage at exposure levels of 0, 25, 150, or 1000 mg/kg/day. Males were dosed from the 14th day prior to mating, during mating until the end of the mating period. Females were dosed from the 14th day prior to the start of the mating phase to day 4 of lactation. Oral dosing of decane produced no evidence of any adverse effects on clinical observations, organ weights, gross pathology, neurobehavioral activity, clinical chemistry or hematology endpoints. Evidence of irritation of the nonglandular mucosa of the stomach was observed, but was considered an artifact of the dosing method and not attributed to the inherent toxicity of the test material. Based on these data, the no-observable- adverse effect level (NOAEL) for repeated dose toxicty was >=1000 mg/kg/day, the highest dose tested.
- Reason / purpose for cross-reference:
- reference to same study
Data source
Reference
- Reference Type:
- study report
- Title:
- Unnamed
- Year:
- 1 995
- Report date:
- 1995
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)
- GLP compliance:
- yes
- Limit test:
- yes
Test material
- Reference substance name:
- Decane
- EC Number:
- 204-686-4
- EC Name:
- Decane
- Cas Number:
- 124-18-5
- Molecular formula:
- C10H22
- IUPAC Name:
- decane
- Details on test material:
- LINPAR 10 (commercial Decane)
approx. composition: 97% 1-decane
Constituent 1
Test animals
- Species:
- rat
- Strain:
- Sprague-Dawley
- Sex:
- male/female
Administration / exposure
- Route of administration:
- oral: gavage
- Vehicle:
- not specified
- Details on oral exposure:
- Males were treated from day 14 prior to the mating phase until the end of the mating phase and then killed, Females were treated from day 14 prior to mating, through day 4 of lactation and then killed.
- Analytical verification of doses or concentrations:
- not specified
- Duration of treatment / exposure:
- Males were treated from day 14 prior to the mating phase until the end of the mating phase and then killed, Females were treated from day 14 prior to mating, through day 4 of lactation and then killed.
- Frequency of treatment:
- 7days/week
Doses / concentrations
- Remarks:
- Doses / Concentrations:
0, 25, 150, or 1000 mg/kg/day (10 ml/kg dosing volume)
Basis:
other: gavage
- No. of animals per sex per dose:
- 10 male, 10 female per group
Control group: 10 male, 10 female, 0.5% methylcellulose - Control animals:
- yes
Examinations
- Observations and examinations performed and frequency:
- Effects on general toxicity, neurobehavioral activity, clinical chemistry, and hematology were evaluated. Gross necropsies and histopathologic examination of tissues were conducted with emphasis on the male reproductive tract.
- Sacrifice and pathology:
- All surviving animals were sacrificed following dosing
- Statistics:
- Adult body and organ weight, food consumption, clinical chemistry, open field activity and hematologic data (raw or transformed) were compared using either parametric or nonparametric (Kruskal-Wallis) ANOVA depending on whether the data were found to be homogeneous or nonhomogeneous using Bartlett's homogeneity of variance procedure. If ANOVA analysis indicated significant differences, Dunnett's test and Mann Whitney's U test, for parametric and nonparemetric data, respectively, were used to analyze for differences between the various dose groups.
Results and discussion
Results of examinations
- Clinical signs:
- no effects observed
- Mortality:
- no mortality observed
- Body weight and weight changes:
- no effects observed
- Food consumption and compound intake (if feeding study):
- no effects observed
- Food efficiency:
- not specified
- Water consumption and compound intake (if drinking water study):
- not examined
- Ophthalmological findings:
- not examined
- Haematological findings:
- no effects observed
- Clinical biochemistry findings:
- no effects observed
- Urinalysis findings:
- no effects observed
- Behaviour (functional findings):
- no effects observed
- Organ weight findings including organ / body weight ratios:
- no effects observed
- Gross pathological findings:
- no effects observed
- Histopathological findings: non-neoplastic:
- no effects observed
- Histopathological findings: neoplastic:
- no effects observed
- Details on results:
- No deaths or clinical signs of toxicity or behavioral changes were noted. No significant differences in body weights or feed consumption were observed. Startle reflex, open field test, and forelimb grip reflex performance data also revealed no treatment-related findings.
There were also no treatment-related changes in hematology or blood chemistry parameters, organ weights or gross pathology. An apparent treatment-related, slight to moderate hyperplasia of the non-glandular mucosa of the stomach, associated with degeneration, hyperkeratosis and submucosal subacute inflammation and, in a few cases, with erosion, was seen in animals of all treated groups. This effect was considered an artifact of the dosing method and not directly related to the toxicity of the test material. No other treatment related histological changes were observed.
Effect levels
- Dose descriptor:
- NOAEL
- Effect level:
- >= 1 000 mg/kg bw/day (nominal)
- Sex:
- male/female
- Basis for effect level:
- other: No treatment-related mortality or significant adverse clinical effects occurred.
Target system / organ toxicity
- Critical effects observed:
- not specified
Applicant's summary and conclusion
- Conclusions:
- Based on these data, the no-observable- adverse effect level (NOAEL) for repeated dose toxicty was >= 1000 mg/kg/day, the highest dose tested.
- Executive summary:
Groups of 10 male and 10 female Sprague Dawley rats were dosed with decane daily by gavage at exposure levels of 0, 25, 150, or 1000 mg/kg/day. Males were dosed from the 14th day prior to mating, during mating until the end of the mating period. Females were dosed from the 14th day prior to the start of the mating phase to day 4 of lactation. Oral dosing of decane produced no evidence of any adverse effects on clinical observations, organ weights, gross pathology, neurobehavioral activity, clinical chemistry or hematology endpoints. Evidence of irritation of the nonglandular mucosa of the stomach was observed, but was considered an artifact of the dosing method and not attributed to the inherent toxicity of the test material. Based on these data, the no-observable- adverse effect level (NOAEL) for repeated dose toxicty was >=1000 mg/kg/day, the highest dose tested.
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