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EC number: 927-344-2 | 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
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- Auto flammability
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- Explosiveness
- Oxidising properties
- Oxidation reduction potential
- Stability in organic solvents and identity of relevant degradation products
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- Additional physico-chemical properties of nanomaterials
- Nanomaterial agglomeration / aggregation
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- Nanomaterial specific surface area
- Nanomaterial Zeta potential
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- Endpoint summary
- Stability
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- 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
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- Genetic toxicity
- Carcinogenicity
- Toxicity to reproduction
- Specific investigations
- Exposure related observations in humans
- Toxic effects on livestock and pets
- Additional toxicological data

Endpoint summary
Administrative data
Key value for chemical safety assessment
Genetic toxicity in vitro
Description of key information
Genetic Toxicity in vitro - Negative
- Bacterial reverse mutation assay (OECD TG 471)
Genetic Toxicity in vitro - Negative - In vitro Mammalian
Chromosome Aberration Test (OECD TG 473)
Genetic Toxicity in vitro - Negative - In vitro Mammalian
Cell Gene Mutation Test (OECD TG 476)
Genetic Toxicity in vitro - Negative - In vitro Sister
Chromatid Exchange Assay in Mammalian Cells (OECD TG 479) - Read-Across
from Hydrodesulfurized Kerosene
Link to relevant study records
- Endpoint:
- in vitro gene mutation study in bacteria
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Study period:
- 1984
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- other: Basic data given:comparable to guidelines/standards.
- Reason / purpose for cross-reference:
- read-across: supporting information
- Reason / purpose for cross-reference:
- reference to same study
- Qualifier:
- equivalent or similar to guideline
- Guideline:
- OECD Guideline 471 (Bacterial Reverse Mutation Assay)
- GLP compliance:
- not specified
- Type of assay:
- bacterial reverse mutation assay
- Species / strain / cell type:
- S. typhimurium, other: TA 1535, TA 1537, TA 1538, TA 98 and TA 100
- Additional strain / cell type characteristics:
- other: histidine dependent
- Metabolic activation:
- with and without
- Metabolic activation system:
- S-9 mix derived from rat liver
- Test concentrations with justification for top dose:
- 8-5000 μg/plate
- Positive controls:
- yes
- Positive control substance:
- benzo(a)pyrene
- Remarks:
- Migrated to IUCLID6: 2-nitrofluorene, 2-aminoanthracene, 9-aminoacridine, N-methyl-N'-nitro-N-nitrosoguanidine
- Details on test system and experimental conditions:
- NUMBER OF REPLICATIONS: 2
- Evaluation criteria:
- Increases in reversion to prototrophy.
- Key result
- Species / strain:
- S. typhimurium, other: TA 1535, TA 1537, TA 1538, TA 98 and TA 100
- Metabolic activation:
- with and without
- Genotoxicity:
- negative
- Cytotoxicity / choice of top concentrations:
- no cytotoxicity
- Positive controls validity:
- valid
- Remarks on result:
- other: all strains/cell types tested
- Remarks:
- Migrated from field 'Test system'.
- Conclusions:
- Interpretation of results: negative
The test substance is not mutagenic both in the presence and absence of S-9. - Executive summary:
An Ames Salmonella typhimurium assay was performed to assess the mutagenicity of BP 8313. Duplicate testing was performed on the strains TA 1535, TA 1537, TA 1538, TA 98, and TA 100, both in the presence and absence of metabolic activation. Test concentrations were between 8-5000 ug/plate. Positive controls substances were benzo(a)pyrene, 2 -nitrofluorene, 2 -aminoanthracene, 9 -aminoacridine, and N-methyl-N'-nitro-N-nitrosoguanadine. Positive control cultures had significantly increased number of revertant colonies. Test substance cultures exhibited no increase in the number of revertant colonies as compared to negative controls in cultures either with or without metabolic activation. The test substance is not mutagenic.
- Endpoint:
- in vitro cytogenicity / chromosome aberration study in mammalian cells
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Study period:
- 1984
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- other: Basic data given:comparable to guidelines/standards.
- Reason / purpose for cross-reference:
- read-across: supporting information
- Reason / purpose for cross-reference:
- reference to same study
- Qualifier:
- equivalent or similar to guideline
- Guideline:
- OECD Guideline 473 (In Vitro Mammalian Chromosome Aberration Test)
- GLP compliance:
- not specified
- Type of assay:
- in vitro mammalian chromosome aberration test
- Species / strain / cell type:
- other: human peripheral lymphocytes
- Metabolic activation:
- with and without
- Metabolic activation system:
- S-9 derived from rat livers
- Test concentrations with justification for top dose:
- 1.2, 6.0, 30.0 μg/ml
- Untreated negative controls:
- yes
- Negative solvent / vehicle controls:
- yes
- Remarks:
- ethanol
- Positive controls:
- yes
- Positive control substance:
- cyclophosphamide
- Details on test system and experimental conditions:
- DURATION
- Exposure duration: 24 hrs
NUMBER OF REPLICATIONS: 2
NUMBER OF CELLS EVALUATED: 100 metaphases examined per culture - Evaluation criteria:
- Mitotic indexes were calculated for every culture. Gross toxcity was determined by the number of metaphases per 1000 cells scored. 100 metaphases were examined per culture and chromosomal aberrations recorded. Metaphases were analyzed for frequency of cells with aberrations, and aberrations other than gaps.
- Statistics:
- Statistical analysis was done on the frequencies of aberrant metaphases, both with and without gap type aberrations. Since there was no significant difference between cultures with and without metabolic acitivation, the data was pooled.
- Key result
- Species / strain:
- other: human peripheral lymphocytes
- Metabolic activation:
- with and without
- Genotoxicity:
- negative
- Cytotoxicity / choice of top concentrations:
- cytotoxicity
- Remarks:
- 140 μg/ml caused a marked reduction in cell growth, 28 μg/ml caused a 58% reduction in mitotic index, 30 μg/ml caused a slight reduction in mitotic index
- Vehicle controls validity:
- valid
- Positive controls validity:
- valid
- Conclusions:
- Interpretation of results: negative
The test substance caused no significant chromosomal damage to human peripheral lymphocytes, therefore the test substance in non-clastogenic. - Executive summary:
An in vitro cytogenic assay was performed on human peripheral lymphocytes to evaluate the clastogenicity of BP 8313. The cells were exposed to 1.2, 6.0, or 30.0 µg/ml of the test substance for 24 hrs, both with and without metabolic activation. Cyclophosphamide was used as a positive control. 100 metaphases were examined from each culture for chromosomal aberrations, and the mitotic index calculated. Since there was little difference in results for cultures with and without metabolic activation, the data were pooled for the statistical analysis. The positive control substance induced significant increases in chromosomal aberrations. The test substance did not increase the number of aberrations in human peripheral lymphocytes as compared to negative controls. The test substance is not clastogenic either in the presence or absence of S-9.
- Endpoint:
- in vitro DNA damage and/or repair study
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Study period:
- 1988
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- other: Equivalent or similar to OECD TG 479.
- Reason / purpose for cross-reference:
- read-across: supporting information
- Qualifier:
- equivalent or similar to guideline
- Guideline:
- OECD Guideline 479 (Genetic Toxicology: In Vitro Sister Chromatid Exchange Assay in Mammalian Cells)
- GLP compliance:
- not specified
- Type of assay:
- sister chromatid exchange assay in mammalian cells
- Species / strain / cell type:
- Chinese hamster Ovary (CHO)
- Metabolic activation:
- with and without
- Metabolic activation system:
- S-9
- Test concentrations with justification for top dose:
- 0, 0.007, 0.013, 0.025, 0.05 uL/mL (without activation)
0, 0.05, 0.1, 0.2, 0.4 uL/mL (with activation) - Vehicle / solvent:
- Acetone
- Untreated negative controls:
- yes
- Negative solvent / vehicle controls:
- yes
- Remarks:
- acetone
- True negative controls:
- yes
- Positive controls:
- yes
- Positive control substance:
- triethylenemelamine
- Details on test system and experimental conditions:
- For the SCE assay CHO cells were seeded in duplicate for each treatment condition and were incubated at 37°C in a humidified atmosphere for 16 to 24 hours. Treatment was carried out by refeeding two complete sets of flasks with complete medium for the non activation study or with S-9 reaction mixture for the activated study to which was added 50 μl of dosing solution of test control or article in solvent or solvent alone. In the non activation study the cells were exposed for about 25 hours. At the end of the treatment period, the treatment medium was removed, the cells rinsed and then exposed to 0.01mM BrdUrd and colcemid (0.1 μg/ml) for a further 2 hours. In the activation study exposure was for 2 hours. After the exposure period, the treatment medium was removed, the cells were washed re-fed with medium containing BrdUrd and then incubated for a further 26 hours. Colcemid was added for the last 2 hours of incubation.For activated and non activated assays metaphase cells were harvested 2 hours after addition of colcemid. Cells were collected and fixed and stored until slides were prepared.
- Evaluation criteria:
- Slides were coded and scored without regard to treatment group. Only cells with 20 ±2 centromeres were selected for evaluation of SCEs. A total of 4 doses were scored including the highest test article dose where sufficient second-division metaphase cells wee available. SCEs were scored in 25 cells from each duplicate culture to make up a total of 50 cells per treatment. The percentage of cells in first (M1), second (M2) or third division (M3) metaphase was also recorded for a total of 100 metaphase cells scored. TEM was used as positive control in the non activated assay at a concentration of 0.025 μg/ml. CP was used in the activation assay at a concentration of 2.5 μg/ml.
- Statistics:
- The test material was considered positive if it induced a doubling in SCE frequency over the solvent control at a minimum of three consecutive dose levels or if a dose responsive and statistically significant increase was observed over a minimum of three dose levels.
- Key result
- Species / strain:
- Chinese hamster Ovary (CHO)
- Metabolic activation:
- with and without
- Genotoxicity:
- negative
- Cytotoxicity / choice of top concentrations:
- no cytotoxicity
- Vehicle controls validity:
- valid
- Untreated negative controls validity:
- valid
- Positive controls validity:
- valid
- Additional information on results:
- The test material was soluble at all concentrations tested. The study in both the presence and absence of S9 was repeated since there was a poor metaphase cell yield. The responses to the positive and negative control materials fulfilled the requirements for the assays. The test material did not cause an increase in SCEs in the absence of exogenous activation. The test material did cause a increase in SCEs at two non adjacent doses (0.05 and 0.4 uL/mL) in the activation assay. However, the increased activity was only seen in one of two treatment flasks. These increases appeared to be random and of no biological significance. It was concluded that the test material was negative in the SCE assay.
- Remarks on result:
- other: all strains/cell types tested
- Remarks:
- Migrated from field 'Test system'.
- Conclusions:
- Interpretation of results: negative
It was concluded that the test material was negative in the SCE assay. - Executive summary:
It was concluded that the test material was negative in the SCE assay.
Referenceopen allclose all
Endpoint conclusion
- Endpoint conclusion:
- no adverse effect observed (negative)
Genetic toxicity in vivo
Description of key information
Genetic Toxicity in vivo - Negative -
Micronucleus Assay in Mouse Bone Marrow (OECD TG 474) - Read-Across from
Jet Fuel A
Genetic Toxicity in vivo - Negative - Mammalian Bone Marrow
Chromosome Aberration Test (OECD TG 475)
Link to relevant study records
- Endpoint:
- in vivo mammalian somatic cell study: cytogenicity / erythrocyte micronucleus
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Study period:
- 1994
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- other: According to or similar to guideline study OECD 474.
- Reason / purpose for cross-reference:
- read-across: supporting information
- Reason / purpose for cross-reference:
- reference to same study
- Qualifier:
- equivalent or similar to guideline
- Guideline:
- OECD Guideline 474 (Mammalian Erythrocyte Micronucleus Test)
- GLP compliance:
- not specified
- Type of assay:
- micronucleus assay
- Species:
- mouse
- Strain:
- CD-1
- Sex:
- male/female
- Details on test animals or test system and environmental conditions:
- TEST ANIMALS
Source: Charles River Breeding Laboratories, Inc.
Sex: Male (65), Female (65)
Age at study initiation: Approximately 9-10 weeks
Weight at study initiation: 23-39g
Housing: Individually
Diet (e.g. ad libitum): Purina Certified Rodent 5002 chow (pellets), ad libitum
Water (e.g. ad libitum): Automatic watering system, ad libitum
Acclimation period: 35d
ENVIRONMENTAL CONDITIONS
Temperature (°F): 68-76
Humidity (%): 40-70%
Photoperiod (hrs dark / hrs light): 12/12 - Route of administration:
- oral: gavage
- Vehicle:
- Corn oil was used. Dose volume did not exceed 10 ml/kg bw.
- Details on exposure:
- The animals were randomly divided into 5 dose groups: 4 of the dose groups contained 30 mice (15 males and 15 females). The animals in the first 4 groups were treated with corn oil (the vehicle control) or with 1.0, 2.5, or 5.0 g/kg test material. Doses were administered by oral gavage: dosing volumes were 10 mL/kg. Five male and five female mice from each group were sacrificed 24, 48, or 72 hr after treatment, and the bone marrows were isolated and examined for the presence of micronuclei. The last test group contained 10 mice (5 males and 5 females), which were given 40 mg/kg cyclophosphamide by intraperitoneal injection. All of these mice were sacrificed 24 hr after test material administration.
- Duration of treatment / exposure:
- Animals were sacrificed 24, 48, and 72 hours after dose administration.
- Frequency of treatment:
- One dose was given of either vehicle control or with 1.0, 2.5, or 5.0 g/kg test material.
- Post exposure period:
- Animals were sacrificed 24, 48, and 72 hours after dose administration.
- Remarks:
- Doses / Concentrations:
0, 1.0, 2.5, or 5.0 g/kg
Basis:
actual ingested
oral gavage - No. of animals per sex per dose:
- The animals were randomly divided into 5 dose groups: 4 of the dose groups contained 30 mice (15 males and 15 females). The animals in the first 4 groups were treated with corn oil (the vehicle control), or with 1.0, 2.5, or 5.0 g/kg test material. Marrows were isolated and examined for the presence of micronuclei. The last test group contained 10 mice (5 males and 5 females), which were given 40 mg/kg cyclophosphamide.
- Control animals:
- yes, concurrent vehicle
- Positive control(s):
- The positive control, cyclophosphamide was administered as a single intraperitoneal injection (40 mg/kg) using water as a carrier.
- Tissues and cell types examined:
- Erythrocytes derived from femur bone marrow.
- Details of tissue and slide preparation:
- Immediately following the sacrifice of the animals, both femurs were removed and the bone marrow was removed and suspended in fetal bovine serum. After the suspension was centrifuged the pellet was resuspended and smears were prepared (two slides per animal).
- Evaluation criteria:
- Slides were stained using acridine orange; polychromatic erythrocytes (PCE) stained red/orange, nonchromatic erythrocytes (NCE) are unstained (dull green), and micronuclei stain bright yellow. Slides were evaluated at 400x by fluorescent microscopy. A total of 1000 erythrocytes were counted from each animal, and the numbers of polychromatic (PCE) and normochromatic (NCE) erythrocytes were tabulated. To determine micronucleus (MN) frequency, 1000 PCEs were examined and the number of MN per 1000 PCEs was reported.
- Statistics:
- Statistical analysis included calculation of means and standard deviations as well as a standard one way analysis of variance (ANOVA) at each time period. When the ANOVA was significant, comparisons of vehicle-treated to dosed group means were made according to Duncans Multiple Range test. A standard regression analysis was performed to test for dose-response relationships. Sexes were analyzed separately.
- Key result
- Sex:
- male/female
- Genotoxicity:
- negative
- Toxicity:
- no effects
- Vehicle controls validity:
- valid
- Negative controls validity:
- not applicable
- Positive controls validity:
- valid
- Additional information on results:
- None of the five test materials produced an increase in micronucleus frequency regardless of sex or sampling time. Additionally, there was no evidence of bone marrow depression. The positive control (cyclophosphamide) produced a significant increase in micronucleus formation, and the vehicle control values fell within the normal control limits.
- Conclusions:
- Interpretation of results: negative
These data indicate that kerosenes are not cytotoxic and are not clastogenic in CD-1 mouse bone marrow cells at doses up to and including 5.0 g/kg of body weight. Classification is not warranted under the new Regulation (EC) 1272/2008 on classification, labeling, and packaging of substances and mixtures (CLP) or under the Directive 67/518/EEC for dangerous substances and Directive 1999/45/EC for preparations. - Executive summary:
Kerosenes were tested in the mammalian bone marrow micronucleus assay using CD-1 mice. The test materials weretested at 24, 48, and 72 hour intervals following exposure and did not induce a statistically significant decrease in the mean percent of polychromatic erythrocytes or an increase in the mean number of micronucleated polychromatic erythrocytes. Both the positive (cyclophosphamide) and the negative (carrier) controls behaved in an appropriate manner. These data indicate that kerosenes are not cytotoxic and are not clastogenic in CD-1 mouse bone marrow cells at doses up to and including 5.0 g/kg of body weight.Classification is not warranted under the new Regulation (EC) 1272/2008 on classification, labeling, and packaging of substances and mixtures (CLP) or under the Directive 67/518/EEC for dangerous substances and Directive 1999/45/EC for preparations.
- Endpoint:
- in vivo mammalian somatic cell study: cytogenicity / bone marrow chromosome aberration
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Study period:
- 1984
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- other: Conducted in accordance with general scientific principles.
- Reason / purpose for cross-reference:
- read-across: supporting information
- Reason / purpose for cross-reference:
- reference to same study
- Qualifier:
- equivalent or similar to guideline
- Guideline:
- OECD Guideline 475 (Mammalian Bone Marrow Chromosome Aberration Test)
- GLP compliance:
- not specified
- Type of assay:
- micronucleus assay
- Species:
- mouse
- Strain:
- Balb/c
- Sex:
- male/female
- Details on test animals or test system and environmental conditions:
- The animals weighed 30 ± 3 g
- Route of administration:
- other: i.p. and inhalation
- Vehicle:
- none
- Details on exposure:
- The animals were sacrified 30 h after i.p. injection of 0.l, 0.05 or 0.01 ml of white spirit. In addition, male animals were allowed to inhale 50 g/m3 of white spirit, during 5 periods of 5 min spaced by intervals of 5min. According to Carpenter et al. (1975) 50 g/m3 represents about 50 times the limit of toxicity. Animals given 200 mg cyclophosphamide per kg b.w. were used as positive controls.
Carpenter C. P., Kinkead E. R., Geary, Jr. D. L., Sullivan L. J., and King J. M. Petroleum Hydrocarbon Toxicity Studies. Ill. Animal and Human Response to Vapors of Stoddard Solvent. 1975. Toxicology and Applied Pharmacology. 32: 282-297.20 ani - Duration of treatment / exposure:
- Experiment #1 - 30 h after i.p. injection of 0.l, 0.05 or 0.01 ml of white spirit
Experiment #2 - male animals were allowed to inhale 50 g/m3 of white spirit, during 5 periods of 5 min spaced by intervals of 5min - Frequency of treatment:
- Experiment #1 - once, animals were sacrificed 30 h after i.p. injection
Experiment #2 - 5 periods of 5 min spaced by intervals of 5min - Post exposure period:
- none
- Remarks:
- Doses / Concentrations:
0, 0.l, 0.05, or 0.01 ml
Basis:
other: i.p. injection - Remarks:
- Doses / Concentrations:
0, 50 g/m3
Basis:
nominal conc.
inhalation - No. of animals per sex per dose:
- 20 animals
- Control animals:
- yes, sham-exposed
- Positive control(s):
- Animals given 200 mg cyclophosphamide per kg b.w. were used as positive controls.
- Tissues and cell types examined:
- micronucleus test; 3000 cells examined per dose
- Details of tissue and slide preparation:
- no data
- Evaluation criteria:
- micronuclei
- Statistics:
- Mann Whitney U-test
- Key result
- Sex:
- male/female
- Genotoxicity:
- negative
- Toxicity:
- no effects
- Vehicle controls validity:
- not applicable
- Negative controls validity:
- valid
- Positive controls validity:
- valid
- Additional information on results:
- see table
- Conclusions:
- Interpretation of results: negative
White spirit did not produce chromosomal aberrations in vivo. - Executive summary:
The ability of white spirit to produce chromosomal aberrations in vivo in mammalian somatic cells was studied by examining eight-week-old BALB/c male and female mice for the presence of micronuclei in the polychromatic erythrocytes from bone marrow.
The animals were sacrified 30 h after i.p. injection of 0.l, 0.05 or 0.01 ml of white spirit. In addition, male animals were allowed to inhale 50 g/m3 of white spirit, during 5 periods of 5 min spaced by intervals of 5min. According to Carpenter et al. (1975) 50 g/m3 represents about 50 times the limit of toxicity. Animals given 200 mg cyclophosphamide per kg b.w. were used as positive controls. When compared to control animals, it was concluded that white spirits are not mutagenic or clastogenic.
Carpenter C. P., Kinkead E. R., Geary, Jr. D. L., Sullivan L. J., and King J. M. Petroleum Hydrocarbon Toxicity Studies.Animal and Human Response to Vapors of Stoddard Solvent. 1975. Toxicology and Applied Pharmacology. 32: 282-297.
Referenceopen allclose all
Treatment |
Cells with micronuclei (%) | |
Male | Female | |
Negative controls |
3.8 | 4.3 |
Cyclophosphamide (200 mg/kg) |
36 |
31 |
White Spirit (0.01mL i.p.) |
4.4 | 3.7 |
White Spirit (0.05mL i.p.) |
4.2 | 4.1 |
White Spirit (0.1mL i.p.) |
4 | 4 |
White Spirit (50g/m3 by inhalation) |
4.1 | N/A |
Endpoint conclusion
- Endpoint conclusion:
- no adverse effect observed (negative)
Additional information
C9-14 Aliphatics (2-25% Aromatics) are not mutagenic using in vitro or in vivo genotoxicity assays. Further data derived from read across data from the supporting substances (structural analogue or surrogate), kerosene and jet fuel, also support the conclusion that C9-14 Aliphatics (2-25% Aromatics) are not genotoxic. In bacterial reverse mutation tests, C9-14 Aliphatics (2-25% Aromatics) were not mutagenic in the presence or absence of metabolic activation. Likewise, there were no mutagenic effects reported in an in vitro mammalian gene mutation test (HGPRT forward mutation assay). No in vitro chromosomal effects were reported in a Chinese hamster ovary assay that examined hydrodesufurized kerosene. The test substance, C9-14 Aliphatics (2-25% Aromatics), did not produce chromosomal effects when tested in an in vivo mouse bone marrow micronucleus assay. These data demonstrate that these substances are not categorizable genotoxins either in vitro or in vivo. Furthermore, no there evidence of hyperplastic responses or pre-neoplastic lesions in sub-chronic and chronic repeat-dose studies in C9-14 Aliphatics (2-25% Aromatics). All studies were conducted in a manner similar or equivalent to currently established OECD guidelines. C9-14 Aliphatics (2-25% Aromatics) are a non-genotoxic agent and classification is not warranted.
Justification for classification or non-classification
The negative results using in vitro and in vivo genotoxicity assays do not warrant the classification of C9-14 Aliphatics (2-25% Aromatics) fluids as genotoxins under the new Regulation (EC) 1272/2008 on classification, labeling and packaging of substances and mixtures (CLP) or under the Directive 67/518/EEC for dangerous substances and Directive 1999/45/EC for preparations.
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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