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EC number: 941-379-0 | 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
Carcinogenicity
Administrative data
Description of key information
Chronic (repeated and prolonged) skin contact with kerosine has the potential to result in tumour formation as a consequence of repeated cycles of irritation, skin damage and repair (similar to OECD 451). In the absence of skin irritation (see key study), no carcinogenic response was seen, indicating a non-genotoxic mechanism mediated by dermal irritation.
Key value for chemical safety assessment
Carcinogenicity: via oral route
Endpoint conclusion
- Endpoint conclusion:
- no study available
Carcinogenicity: via inhalation route
Endpoint conclusion
- Endpoint conclusion:
- no study available
Carcinogenicity: via dermal route
Link to relevant study records
- Endpoint:
- carcinogenicity: dermal
- Type of information:
- read-across from supporting substance (structural analogue or surrogate)
- Adequacy of study:
- key study
- Study period:
- Not reported
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- other: see 'Remark'
- Remarks:
- This study is classified as reliable with restrictions because the use of secondary sources of data is acceptable when they are based on a critical evaluation of peer-reviewed data and a consequent selection of a reliable and representative value for the property under investigation. The introduction to the Overview of the CONCAWE Middle Distillate Programme states that the report reviewed the results from a three phase programme of work designed to investigate the factors influencing the skin carcinogenicity of middle distillates. Therefore, although the proprietary study report is not available, the values presented here are acceptable as they are from a reliable secondary source of mammalian toxicity data.
- Justification for type of information:
- Read across justification included in Section 13
- Reason / purpose for cross-reference:
- read-across: supporting information
- Qualifier:
- equivalent or similar to guideline
- Guideline:
- OECD Guideline 451 (Carcinogenicity Studies)
- Deviations:
- yes
- GLP compliance:
- yes
- Species:
- mouse
- Strain:
- C3H
- Sex:
- male
- Details on test animals or test system and environmental conditions:
- TEST ANIMALS
- Source: Not reported
- Age at study initiation: Not reported
- Weight at study initiation: Not reported
- Housing: Individually
- Diet (e.g. ad libitum): ad libitum
- Water (e.g. ad libitum): ad libitum
- Acclimation period: Not reported
ENVIRONMENTAL CONDITIONS: details not provided, only stated as controlled environmental conditions.
IN-LIFE DATES: Not reported - Route of administration:
- dermal
- Vehicle:
- other: high-dose undiluted, lower doses diluted with mineral oil
- Details on exposure:
- Groups of 50 male C3H mice were treated with the test material. Three dosing regimes were employed, each using a standard dose volume of 50 microlitres. These were designed to ensure that each group received the equal weekly dose of test material regardless of dilution. The three regimes were:
100%, applied 2 times per week (expected to cause irritation)
50%, applied 4 times per week (expected to cause slight irritation)
28.5%, applied 7 times per week (expected to be non-irritating)
This was intended to clarify the role of skin irritation in skin tumour formation. The diluent used was a highly refined non-irritating mineral oil. Control groups consisted of a positive control, using heavy clarified oil known to be carcinogenic, and a vehicle control, using the highly refined mineral oil.
Skin irritation was assessed daily, using a numerical scoring system. Animals were examined weekly for evidence of dermal growths or other signs of toxicity. All animals were sacrificed, either when considered moribund, suspected of having a carcinoma, or after 104 weeks treatment, and were subject to detailed necropsy examination.
TEST SITE
- Area of exposure: Not reported
- % coverage: Not reported
- Type of wrap if used: Not reported
- Time intervals for shavings or clippings: Not reported
REMOVAL OF TEST SUBSTANCE
- Washing (if done): Not reported
- Time after start of exposure: Not reported
TEST MATERIAL
- Amount(s) applied (volume or weight with unit): 50 microlitres
- Concentration (if solution): 28.5 or 50% solution in mineral oil
- Constant volume or concentration used: Yes
VEHICLE
- Justification for use and choice of vehicle (if other than water): Based on results from phase 2 (subchronic toxicity)
- Concentration (if solution): 28.5 or 50% solution
- Purity: Not reported
USE OF RESTRAINERS FOR PREVENTING INGESTION: No - Analytical verification of doses or concentrations:
- no
- Details on analytical verification of doses or concentrations:
- Not applicable
- Duration of treatment / exposure:
- 2 years
- Frequency of treatment:
- Low dose: 7 days a week, mid dose: 4 days a week, high dose: twice a week
- Post exposure period:
- No
- Remarks:
- Doses / Concentrations:
0, 28.5, 50, or 100%
Basis:
nominal conc. - No. of animals per sex per dose:
- Fifty males
- Control animals:
- yes, concurrent vehicle
- Details on study design:
- - Dose selection rationale: Based on subchronic study
- Rationale for animal assignment (if not random): Not reported - Positive control:
- Heavy clarified oil (HCO)
- Observations and examinations performed and frequency:
- CAGE SIDE OBSERVATIONS: No data
DETAILED CLINICAL OBSERVATIONS: No data
DERMAL IRRITATION (if dermal study): Yes
- Time schedule for examinations: Throughout the study
BODY WEIGHT: No data
FOOD CONSUMPTION:
- Food consumption for each animal determined and mean daily diet consumption calculated as g food/kg body weight/day: No data
FOOD EFFICIENCY:
- Body weight gain in kg/food consumption in kg per unit time X 100 calculated as time-weighted averages from the consumption and body weight gain data: No
WATER CONSUMPTION: No
OPHTHALMOSCOPIC EXAMINATION: No
HAEMATOLOGY: No
CLINICAL CHEMISTRY: No
URINALYSIS: No
NEUROBEHAVIOURAL EXAMINATION: No - Sacrifice and pathology:
- GROSS PATHOLOGY: Yes
HISTOPATHOLOGY: Yes, apparently only on the gross skin lesions - Other examinations:
- None detailed
- Statistics:
- None reported
- Clinical signs:
- effects observed, treatment-related
- Mortality:
- mortality observed, treatment-related
- Body weight and weight changes:
- not specified
- Food consumption and compound intake (if feeding study):
- not specified
- Food efficiency:
- not examined
- Water consumption and compound intake (if drinking water study):
- not examined
- Ophthalmological findings:
- not examined
- Haematological findings:
- not examined
- Clinical biochemistry findings:
- not examined
- Urinalysis findings:
- not examined
- Behaviour (functional findings):
- not examined
- Organ weight findings including organ / body weight ratios:
- not examined
- Gross pathological findings:
- effects observed, treatment-related
- Histopathological findings: non-neoplastic:
- not examined
- Histopathological findings: neoplastic:
- effects observed, treatment-related
- Details on results:
- CLINICAL SIGNS AND MORTALITY: The pattern of mortality in animals from the 28.5% treatment groups was generally similar to that of the mineral oil (negative) control group, with slightly higher mortality in the 50% or 100% groups. Groups treated with undiluted kerosine or 50% kerosine had the lowest survival rate. Survival in the positive control group (median 300 days) was also significantly lower than the controls (median 582 days). Dermal irritation was observed in the positive- and negative control substances, and was generally greater after treatment with neat distillate twice per week compared with more frequent treatment with lower concentrations.
GROSS PATHOLOGY: There were no significant treatment-related gross findings at necropsy other than skin irritation and masses (tumours) at the treatment site.
HISTOPATHOLOGY: NEOPLASTIC : Benign and/or malignant skin tumours were diagnosed at the application site in several of the groups, and were frequent in the positive control group where a total of 164 tumours (88 benign, 73 malignant) developed in 47 mice with 217 days to first tumour. This contrasts with the negative control group which was tumour free. Tumours were observed only in the high dose group of mice. No mice had tumours in the middle and low dose groups. - Relevance of carcinogenic effects / potential:
- An undiluted hydrotreated straight-run kerosine appeared to produce tumours by a non-genotoxic mechanism involving skin irritation.
- Conclusions:
- An undiluted hydrotreated straight-run kerosine was considered to produce skin tumours by a non-genotoxic mechanism involving skin irritation.
- Executive summary:
The potential influence of skin irritation on tumour development in long-term mouse skin painting studies was investigated as part of the CONCAWE middle distillates programme. The study included straight run hydrotreated kerosine (MD3). This was tested alongside a negative control (highly refined, non-irritating mineral oil) and a positive control treatment (heavy clarified oil (HCO), 5% in mineral oil).
Groups of 50 male C3H/HeNCrlBR VAF/Plus® mice were individually housed in stainless steel cages, and the various test (28.5%, 50%, or 100%) or control materials applied regularly to clipped dorsal skin. The treatment regime was designed to deliver a constant total weekly dose of each distillate while varying the extent of any local skin irritation by manipulating test material concentration and frequency of application.
Of the 3 groups treated with hydrotreated kerosine, only the group treated with undiluted material developed skin tumours. Twelve animals developed a total of 20 tumours (6 benign,14 malignant).
There were no significant treatment-related gross findings at necropsy other than skin irritation and masses (tumours) at the treatment site. Benign and/or malignant skin tumours were diagnosed at the application site in several of the groups, and were frequent in the positive control group where a total of 164 tumours (88 benign, 73 malignant) developed in 47 mice with 217 days to first tumour. This contrasts with the negative control group which was tumour free. Tumours occurred only in the high dose group treated with MD3 (441 days until the first tumour).
For the hydrotreated straight run kerosine, skin tumours only developed in the group of animals in which substantial skin irritation occurred during the study. Since no PACs were detected in the straight run kerosine it is concluded that the occurrence of tumours is likely to have been caused by a non-genotoxic mechanism. This conclusion is consistent with reports by others that lighter middle distillates are tumour promoters but not initiators and furthermore that skin irritation plays an important role in skin tumour development.
This study received a Klimisch score of 2 and is classified as reliable with restrictions because the use of secondary sources of data is acceptable when they are based on a critical evaluation of peer-reviewed data and a consequent selection of a reliable and representative value for the property under investigation. The introduction to the Overview of the CONCAWE Middle Distillate Programme states that the report reviewed the results from a three phase programme of work designed to investigate the factors influencing the skin carcinogenicity of middle distillates. Therefore, although the proprietary study report is not available, the values presented here are acceptable as they are from a reliable secondary source of mammalian toxicity data.
Reference
Table 1. Skin tumour incidence
Treatment |
% |
Days to first tumour |
Number of histologically confirmed tumours |
|||||
squamous cell carcinoma |
papilloma |
kerato-acanthoma |
basal cell carcinoma |
fibro- |
melanoma |
|||
Mineral oil |
100 |
- |
- |
- |
- |
- |
- |
- |
HCO |
5 |
217 |
73 |
88 |
3 |
- |
- |
- |
MD3 |
28.5 |
- |
- |
- |
- |
- |
- |
- |
|
50 |
- |
- |
- |
- |
- |
- |
- |
|
100 |
441 |
7 |
6 |
- |
1 |
3/5* |
- |
* number of animals with specified tumour / total number of tumours per group.
Endpoint conclusion
- Endpoint conclusion:
- no adverse effect observed
Justification for classification or non-classification
Jet fuels and kerosines were not found to be mutagenic or genotoxic, and the observations from animal studies confirm the non-genotoxic nature of the skin tumour formation. Although dermal irritation alone seems not sufficient to cause dermal tumourigenicity, studies clearly show that dermal irritation and inflammation are prerequisites for dermal carcinogenicity. In studies where dermal irritation and/or inflammation were prevented but other factors, such as dermal uptake of polycyclic aromatic compounds were kept identical, no skin tumours were observed. Based on this data, kerosines are classified as non-carcinogenic according to the EU CLP Regulation (EC No. 1272/2008).
.Additional information
Data on related substances have been used to 'read-across' and predict the hazard properties. A 'read-across' justification document can be found in section 13.
The potential of petroleum hydrocarbons to induce skin tumours is generally considered to be largely dependent on the presence of polycyclic aromatic compounds. Middle distillate fractions such as kerosine however contain relatively low concentrations of polycyclic aromatic compounds and are non-genotoxic in both in vitro and in vivo test systems. Nevertheless in some mouse epidermal carcinogenesis studies they do give rise to skin tumours. This carcinogenic response is characterized by a long latency, with only a small percentage of animals developing tumours compared to the response triggered by polycyclic aromatic compounds which are known to be skin carcinogens. Numerous studies have shown that chronic irritation and inflammation promote the development of skin tumours, whilst prevention of chronic skin irritation precludes the formation of dermal tumours.
Hydrodesulfurised kerosine (CAS # 64742-81-0) was tested in a standard 2-year bioassay in C3H/HeJ mice (API, 1989). The animals, 50 per group, were treated twice weekly with 50 μl of neat hydrodesulfurised kerosine. As positive controls, two groups of 50 mice were exposed twice weekly to 50 μl of 0.01% or 0.05% benzo(a)pyrene in toluene, respectively. Two negative control groups received either 50 μl toluene or no treatment. Animals in all groups but the negative control group with no treatment at all showed varying degrees of dermal irritation; dermal lesions in the toluene control group were less than in the test group.
In all test groups dermal tumours developed. The mean latency time for tumour formation in the hydrodesulfurised kerosine treated group was 76 weeks, significantly longer than the 47 weeks observed in the 0.05% benz(a)pyrene treated group. The number of tumours, 1 benign and 19 malignant, in the 41 surviving mice was also significantly less than in the benzo(a)pyrene treated groups (11 benign and 13 malignant tumours in the 0.01% benzo(a)pyrene group and 2 benign and 44 malignant in the 0.05% benzo(a)pyrene group) whilst the toluene group showed no dermal tumours(44 mice surviving). It was concluded that under the conditions of the test, hydrodesulfurised kerosine was a skin carcinogen.
The potential influence of skin irritation on tumour development in long-term mouse skin painting studies was investigated as part of the CONCAWE middle distillates programme (Dally et al 1996, Nessel 1999, Exxon 1996). The study included straight run hydrotreated kerosine (MD3). This was tested alongside a negative control (highly refined, non-irritating mineral oil) and a positive control treatment (heavy clarified oil (HCO), 5% in mineral oil). Groups of 50 male C3H/HeNCrlBR VAF/Plus® mice were individually housed in stainless steel cages, and the various test (28.5%, 50%, or 100%) or control materials applied regularly to clipped dorsal skin. The treatment regime was designed to deliver a constant total weekly dose of each distillate while varying the extent of any local skin irritation by manipulating test material concentration and frequency of application.
For the straight run hydrotreated kerosine, skin tumours only developed in the group of animals in which substantial skin irritation occurred during the study. Since no PACs were detected in the material it was concluded that the occurrence of tumours is likely to have been caused by a non-genotoxic mechanism. This conclusion is consistent with reports by others (Skisak 1991) that lighter middle distillates are tumour promotors but not initiators and furthermore that skin irritation plays an important role in skin tumour development. These tumours are probably the consequence of a continuous cycle of cell damage and repair caused by chronic skin irritation.
The conclusions gained from this study can be applied to other carcinogenicity studies on kerosines, and they show that tumours are noted in the presence of repeated dermal irritation, and that kerosines lack a genotoxic mechanism of carcinogenicity.
Justification for selection of carcinogenicity via dermal route endpoint:
Part of a well conducted research programme to investigate the role of skin irritation in the development of skin tumours following repeated application of petroleum middle distillate fractions to the skin of mice
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