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EC number: 920-360-0 | 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 somatic cell study: cytogenicity / bone marrow chromosome aberration
- Remarks:
- Ty
- Type of information:
- read-across from supporting substance (structural analogue or surrogate)
- Adequacy of study:
- key study
- Study period:
- 1984
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- other: According to or similar to guideline study OECD 475: 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-reference
- Reason / purpose for cross-reference:
- read-across: supporting information
Reference
- Endpoint:
- in vivo mammalian somatic cell study: cytogenicity / bone marrow chromosome aberration
- Type of information:
- read-across from supporting substance (structural analogue or surrogate)
- Adequacy of study:
- key study
- Study period:
- 1984
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- other: According to or similar to guideline study OECD 475: 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
- Key result
- Sex:
- male/female
- Genotoxicity:
- negative
- Toxicity:
- not examined
- Vehicle controls validity:
- not applicable
- Negative controls validity:
- valid
- Positive controls validity:
- valid
- Additional information on results:
- The data are given in the report for males, females and as male and female pooled data. When the results for males were compared with those for controls and the females were compared to controls, no statistically significant differences were found. The data summarized below, are the pooled data for males and females. The structural aberration frequency did not differ significantly from the negative control at any tested dose. The percentage of cells showing one or more structural aberrations or 2 or more structural aberrations were also similar to the negative controls. A concurrent positive control group induced significant increases in aberrations.
- Conclusions:
- Interpretation of results: negative
The test material did not cause chromosome aberration in the test model. - Executive summary:
This data is being read across from the source study that tested Hydrodesulfurized kerosene based on analogue read across.
The test material did not cause chromosome aberration in the test model.
Data source
Reference
- Reference Type:
- study report
- Title:
- Unnamed
- Year:
- 1 984
Materials and methods
Test guideline
- Qualifier:
- equivalent or similar to guideline
- Guideline:
- OECD Guideline 475 (Mammalian Bone Marrow Chromosome Aberration Test)
- GLP compliance:
- yes
- Type of assay:
- chromosome aberration assay
Test material
- Reference substance name:
- Hydrodesulfurized kerosene
- IUPAC Name:
- Hydrodesulfurized kerosene
- Reference substance name:
- Kerosine (petroleum), hydrodesulfurized
- EC Number:
- 265-184-9
- EC Name:
- Kerosine (petroleum), hydrodesulfurized
- Cas Number:
- 64742-81-0
- IUPAC Name:
- 64742-81-0
- Details on test material:
- Kerosene, hydrodesulfurized (CAS No. 64742-81-0)
Constituent 1
Constituent 2
Test animals
- Species:
- rat
- Strain:
- Sprague-Dawley
- Sex:
- male/female
Administration / exposure
- Route of administration:
- intraperitoneal
- Details on exposure:
- A pilot study was carried out in 4 male and 4 female young adult Sprague Dawley rats. These animals were given a single intraperitoneal (i.p.) dose (3 g/kg) of API 81-07. During the following 48 hours observation, no animals died. The doses selected for the cytogenetics study were therefore 0.3, 1 and 3 g/kg. Three groups of 15 male and 15 female rats were given a single i.p. dose of either 0.3, 1 or 3 g API 81-07/kg. At six, 24 and 48 hours after dosing 5 males and 5 females were killed at each dose level. An additional 15 males and 15 females were untreated and served as negative controls. These animals were otherwise treated the same as the test animals. A positive control group of 5 males and 5 females was administered 0.8 mg/kg Triethylenemelamine (TEM) as a single i.p. dose. These positive control animals were killed 24 hours after administration of the positive control substance. Three hours prior to being killed with CO2, animals were injected i.p. with 4 mg/kg of colchicine. After the animal was killed, the adhering soft tissue and epiphyses of both tibiae were removed and the marrow was flushed from the bone and transferred to Hank's balanced salt solution. The marrow button was collected by centrifugation and was then re suspended in 0.075M KCl. The centrifugation was repeated and the pellet resuspended in fixative (methanol:acetic acid, 3:1). The fixative was changed once and left overnight. Cells in fixative were dropped onto glass slides which were then air dried and stained with Giemsa. Slides were coded and scored for chromosomal aberrations. 50 spreads were read for each animal where feasible. A mitotic index based on at least 500 counted cells was also recorded. The index was calculated by scoring the number of cells in mitosis per 500 cells on each read slide.
- Duration of treatment / exposure:
- Three groups of 15 male and 15 female rats were given a single i.p. dose of either 0.3, 1 or 3 g API 81-07/kg. At six, 24 and 48 hours after dosing 5 males and 5 females were killed at each dose level. An additional 15 males and 15 females were untreated and served as negative controls.
- Frequency of treatment:
- Single i.p. dose of either 0.3, 1 or 3 g API 81-07/kg
Doses / concentrations
- Remarks:
- Doses / Concentrations:
0, 0.3, 1 or 3 g/kg.
Basis:
analytical conc.
i.p.
- No. of animals per sex per dose:
- 15 male and 15 female rats
- Control animals:
- yes, concurrent no treatment
- Positive control(s):
- These animals were otherwise treated the same as the test animals. A positive control group of 5 males and 5 females was administered 0.8 mg/kg Triethylenemelamine (TEM) as a single i.p. dose. These positive control animals were killed 24 hours after administration of the positive control substance.
Examinations
- Details of tissue and slide preparation:
- Three hours prior to being killed with CO 2 , animals were injected i.p. with 4 mg/kg of colchicine. After the animal was killed, the adhering soft tissue and epiphyses of both tibiae were removed and the marrow was flushed from the bone and transferred to Hank's balanced salt solution. The marrow button was collected by centrifugation and was then resuspended in 0.075M KCl. The centrifugation was repeated and the pellet re suspended in fixative (methanol:acetic acid, 3:1). The fixative was changed once and left overnight. Cells in fixative were dropped onto glass slides which were then air dried and stained with Giemsa. Slides were coded and scored for chromosomal aberrations. 50 spreads were read for each animal where feasible. A mitotic index based on at least 500 counted cells was also recorded. The index was calculated by scoring the number of cells in mitosis per 500 cells on each read slide.
- Evaluation criteria:
- Data interpretation and evaluation Gaps were not counted as significant aberrations. Open breaks were considered as indicators of genetic damage as were configurations resulting from the repair of breaks. The latter included translocations, multiradials, rings, multicentrics, etc. Reunion figures such as these were weighed slightly higher than breaks since they usually resulted from more than one break. Cells with more than one aberration were considered to indicate more genetic damage than those with evidence of single events. Consistent variations from the euploid number were also considered in the evaluation of mutagenic potential.
The type of aberration, its frequency and its correlation to dose in a given time was considered in evaluating the test material as being positive or negative. - Statistics:
- Statistical evaluation Performed by Student's t-tests on four parameters:
1. Number of structural aberrations per animal
2. Number of numerical aberrations per animal
3. % cells with one or more structural aberrations per animal
4. % cells with 2 or more structural aberrations per animal.
Results and discussion
Test results
- Key result
- Sex:
- male/female
- Genotoxicity:
- negative
- Toxicity:
- not examined
- Vehicle controls validity:
- not applicable
- Negative controls validity:
- valid
- Positive controls validity:
- valid
- Additional information on results:
- The data are given in the report for males, females and as male and female pooled data. When the results for males were compared with those for controls and the females were compared to controls, no statistically significant differences were found. The data summarized below, are the pooled data for males and females. The structural aberration frequency did not differ significantly from the negative control at any tested dose. The percentage of cells showing one or more structural aberrations or 2 or more structural aberrations were also similar to the negative controls. A concurrent positive control group induced significant increases in aberrations.
Applicant's summary and conclusion
- Conclusions:
- Interpretation of results: negative
The test material did not cause chromosome aberration in the test model. - Executive summary:
The test material did not cause chromosome aberration in the test model.
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