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EC number: 921-024-6 | 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
Genetic toxicity: in vivo
Administrative data
- Endpoint:
- in vivo mammalian germ cell study: cytogenicity / chromosome aberration
- Remarks:
- Type of genotoxicity: chromosome aberration
- Type of information:
- read-across from supporting substance (structural analogue or surrogate)
- Adequacy of study:
- key study
- Study period:
- July 1978 - January 1980
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- other: Comparable to guideline with acceptable restrictions.
- Justification for type of information:
- A discussion and report on the read across strategy is given as an attachment in IUCLID Section 13.
Cross-reference
- Reason / purpose for cross-reference:
- read-across: supporting information
Reference
- Endpoint:
- in vivo mammalian germ cell study: cytogenicity / chromosome aberration
- Remarks:
- Type of genotoxicity: chromosome aberration
- Type of information:
- read-across from supporting substance (structural analogue or surrogate)
- Adequacy of study:
- key study
- Study period:
- July 1978 - January 1980
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- other: Comparable to guideline with acceptable restrictions.
- 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
- Key result
- Sex:
- male/female
- Genotoxicity:
- negative
- Remarks:
- At dose level of 400 and 1200 ppm the test substance was not mutagenic in rats by the dominant-lethal test.
- Toxicity:
- no effects
- Vehicle controls validity:
- other: no vehicle was used
- Negative controls validity:
- valid
- Positive controls validity:
- valid
- Conclusions:
- Interpretation of results: negative
Under the conditions of the test no negative effects were induced by the test substance, hydrocarbons, C7-C9, isoalkanes. - Executive summary:
This data is being read across from the source study that tested Hydrocarbon C7-C9, isoalkanes based on analogue read across.
Under the conditions of the test no negative effects were induced by the test substance, hydrocarbons, C7 -C9, isoalkanes.
No treatment-related effects were observed for mortality, in-life physical or necropsy examinations and for body weights in males.
No treatment effect was indicated from microscopic evaluation of testes, seminal vesicles, epididymides and prostate tissues from 5 randomly chosen males from each exposure group.
In one animal of the 400 ppm exposure group a caseous mass was observed in the left epididymis. This caseous mass was seen microscopically to be a spermatic granuloma. Since this was observed in a single animal, this is not considered to be treatment related. Several animals (one in control, one in 100 ppm group, one in 1200 ppm group) presented a purulent prostatitis which was of probable bacterial etiology.
Pregnancy rates, implantation data and implantation efficiency values and fetal death data for females mated to treated males were considered comparable to data for females mated to negative control males for each week of the post-treatment mating period. At dose level of 400 and 1200 ppm the test substance was not mutagenic in rats by the dominant-lethal test.
Positive control:
Females mated to the positive control males had fewer implants and lower implantation efficiency values (indicative of pre-implantation loss) than females mated to the negative control males. Fetal death parameters (mean and expressed as a percentage of total implants) for these same females were significantly increased during the post-treatment mating interval.
Data source
Reference
- Reference Type:
- study report
- Title:
- Unnamed
- Year:
- 1 980
- Report date:
- 1980
Materials and methods
Test guideline
- Qualifier:
- equivalent or similar to guideline
- Guideline:
- OECD Guideline 478 (Genetic Toxicology: Rodent Dominant Lethal Test)
- Principles of method if other than guideline:
- Similar to OECD 478, only two dose levels were used.
- GLP compliance:
- not specified
- Type of assay:
- rodent dominant lethal assay
Test material
- Reference substance name:
- Hydrocarbons, C7-C9, isoalkanes
- EC Number:
- 921-728-3
- Molecular formula:
- None available - not a single isomer - see remarks
- IUPAC Name:
- Hydrocarbons, C7-C9, isoalkanes
- Details on test material:
- - Name of test material (as cited in study report): MRD-78-26
- Molecular weight: 114 g/M
- Substance type: colourless liquid
- Physical state: colourless liquid
- Analytical purity: 100% pure commercial product
- Storage condition of test material: storage shed
Constituent 1
Test animals
- Species:
- rat
- Strain:
- Sprague-Dawley
- Sex:
- male/female
- Details on test animals or test system and environmental conditions:
- TEST ANIMALS
- Source: Charles River Breeding Laboratories, Wilmington, Massachusetts
- Age at study initiation: males: 10 weeks at initiation of pre-treatment mating period; females: 9 weeks at initiation of week 1 of pre-treatment mating period; females: 8 weeks at initiation of week 1 of post-treatment mating period
- Housing: males: individually housing during the treatment period; females: individually housing during the pre- and post-mating period
- Diet: Purina Laboratory Chow; ad libitum; except chamber-exposed groups during the treatment period
- Water: ad libitum; except chamber-exposed groups during the treatment period
Administration / exposure
- Route of administration:
- inhalation
- Vehicle:
- none
- Details on exposure:
- TYPE OF INHALATION EXPOSURE: whole body
GENERATION OF TEST ATMOSPHERE / CHAMBER DESCRIPTION
- Exposure apparatus: The stainless steel and glass chambers had a total volume of one cubic metre with an effective volume of 760 L.
- Air flow rate: 132 L/min
- Air change rate: every 7.6 min
- The test substance was placed in fritted-bottom, gas-washing bottles. Dry air, at various flow rates, was passed through the test material and the vapour-air mixtures entered the chamber air inlets and were further diluted with room air to provide the desired concentrations.
TEST ATMOSPHERE
Atmospheric sampling was performed using a Wilks Scientific Corp., Miran IA Ambient Air Analyzer (long pathlength infrared). On each exposure day three samples were drawn from each exposure chamber (at 1, 3 and 5 hours) and the exposure concentrations calculated by comparing the absorption of this sample to the standard curve. - Duration of treatment / exposure:
- 8 consecutive weeks
- Frequency of treatment:
- 6 hours/day, 5 days/week
- Post exposure period:
- 4 weeks
Doses / concentrations
- Remarks:
- Doses / Concentrations:
400 and 1200 ppm
Basis:
nominal conc.
- No. of animals per sex per dose:
- only males were exposed: 10/group
- Control animals:
- yes, sham-exposed
- Positive control(s):
- triethylenemelamine
- Route of administration: intraperitoneally on a single day, at least 2 hours prior to mating
- Doses level/ volume: 0.5 mg/kg body weight; 1 mL/kg body weight
- Vehicle: 0.9 % injectable normal saline solution
Examinations
- Tissues and cell types examined:
- Males: testes, seminal vesicles, epididymides, prostate tissues
Females: uteri - Details of tissue and slide preparation:
- METHOD OF ANALYSIS:
Males: Seminal vesicles, epididymides, prostate and any abnormal lesion or tissue masses were preserved in 10 % neutral buffered formalin. Testes were stored for 48 hours in Bouin´s solution and subsequently placed in formalin. Tissues from 5 randomly chosen males from each group were examined.
Females: The uteri from all females (pregnant and non-pregnant) were appropriately identified and preserved intact in a 10 % neutral buffered formalin solution. - Statistics:
- Comparisons were made during the treatment and post-treatment periods between negative control, positive control and test substance-treated groups by the Chi-square test. Absolute data were compared by using the F-test and Student´s t-test. When variances differed significantly, Student´s t-test was appropriately modified using Cochran´s approximation (t´). Corpora lutea and implantation data were evaluated by the one-tailed test.
Results and discussion
Test results
- Key result
- Sex:
- male/female
- Genotoxicity:
- negative
- Remarks:
- At dose level of 400 and 1200 ppm the test substance was not mutagenic in rats by the dominant-lethal test.
- Toxicity:
- no effects
- Vehicle controls validity:
- other: no vehicle was used
- Negative controls validity:
- valid
- Positive controls validity:
- valid
Any other information on results incl. tables
No treatment-related effects were observed for mortality, in-life physical or necropsy examinations and for body weights in males.
No treatment effect was indicated from microscopic evaluation of testes, seminal vesicles, epididymides and prostate tissues from 5 randomly chosen males from each exposure group.
In one animal of the 400 ppm exposure group a caseous mass was observed in the left epididymis. This caseous mass was seen microscopically to be a spermatic granuloma. Since this was observed in a single animal, this is not considered to be treatment related. Several animals (one in control, one in 100 ppm group, one in 1200 ppm group) presented a purulent prostatitis which was of probable bacterial etiology.
Pregnancy rates, implantation data and implantation efficiency values and fetal death data for females mated to treated males were considered comparable to data for females mated to negative control males for each week of the post-treatment mating period. At dose level of 400 and 1200 ppm the test substance was not mutagenic in rats by the dominant-lethal test.
Positive control:
Females mated to the positive control males had fewer implants and lower implantation efficiency values (indicative of pre-implantation loss) than females mated to the negative control males. Fetal death parameters (mean and expressed as a percentage of total implants) for these same females were significantly increased during the post-treatment mating interval.
Applicant's summary and conclusion
- Conclusions:
- Interpretation of results: negative
Under the conditions of the test no negative effects were induced by the test substance, hydrocarbons, C7-C9, isoalkanes. - Executive summary:
Under the conditions of the test no negative effects were induced by the test substance, hydrocarbons, C7 -C9, isoalkanes.
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