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EC number: 297-854-1 | CAS number: 93763-35-0 A complex combination of hydrocarbons obtained as solvents which have been subjected to hydrotreatment in order to convert aromatics to naphthenes by catalytic hydrogenation.
- 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
Basic toxicokinetics
Administrative data
- Endpoint:
- basic toxicokinetics in vivo
- Type of information:
- migrated information: read-across based on grouping of substances (category approach)
- Adequacy of study:
- key study
- Reliability:
- 1 (reliable without restriction)
Data source
Reference
- Reference Type:
- study report
- Title:
- Unnamed
- Year:
- 1 994
Materials and methods
- Objective of study:
- absorption
Test guideline
- Qualifier:
- no guideline available
- GLP compliance:
- yes
Test material
- Reference substance name:
- Blend of 64742-81-0 & 64741-77-1
- IUPAC Name:
- Blend of 64742-81-0 & 64741-77-1
- Reference substance name:
- md 8 (blend)
- IUPAC Name:
- md 8 (blend)
- Test material form:
- other: low viscosity liquid hydrocarbon
- Details on test material:
- Blend of straight run hydrotreated kerosine (30%) and hydrocracked kerosine (70%)
Composition %: Saturates 76.3, Aromatics 21.8 and Olefins 1.9
Constituent 1
Constituent 2
- Radiolabelling:
- yes
- Remarks:
- 14C-labelled naphthalene or 14C-labelled n-tetradecane
Test animals
- Species:
- mouse
- Strain:
- C3H
- Sex:
- male
Administration / exposure
- Route of administration:
- dermal
- Vehicle:
- other: mineral oil
- Duration and frequency of treatment / exposure:
- 96 hour(s)
Doses / concentrations
- Remarks:
- Doses / Concentrations:
Males: 15 µl undiluted and 60 µl diluted to 25% with mineral oil
- No. of animals per sex per dose / concentration:
- Males: 5
Results and discussion
Toxicokinetic / pharmacokinetic studies
Toxicokinetic parametersopen allclose all
- Toxicokinetic parameters:
- half-life 1st:
- Toxicokinetic parameters:
- half-life 2nd:
- Toxicokinetic parameters:
- half-life 3rd:
Any other information on results incl. tables
In
the study with dermally applied undiluted test material approximately 5%
of the labelled tetradecane and 15% of the labelled naphthalene was absorbed
over 96 hours. In the study with the 25% concentration of test material,
approximately 7%
of the labelled tetradecane and 16% of the labelled naphthalene was absorbed
over 96 hours.
In the passive inhalation study approximately 2.8% (undiluted test material)
and 1.8% (25% concentration) of the labelled naphthalene was absorbed. In
contrast, approximately 0.2% of labelled tetradecane in undiluted
and diluted test material was absorbed.
These studies demonstrate that dilution of the test material in mineral oil
did not influence absorption of the radiolabelled
"spikes" present.
Applicant's summary and conclusion
- Conclusions:
- Interpretation of results (migrated information): low bioaccumulation potential based on study results constituents of kerosine are absorbed through the skin
Comparison of data from testing with undiluted material and data, obtained with a 25% concentration of the test compounds diluted in mineral oil, revealed that the difference in absorption of the radiolabelled "spikes" was insignificant, therefore it can be concluded that dilution did not affect the absorption of the test compound. The difference in absorption of 14C-labelled naphthalene or 14C-labelled n-tetradecane, showed that aromatics are absorbed better than saturates. - Executive summary:
The test material (blend of straight run hydrotreated kerosine (30%) and hydrocracked kerosine (70%)) was fortified before dosing with either 14C-labelled naphthalene or 14C-labelled n-tetradecane as surrogates representing the aromatic and saturates fraction. Either 15 µl of undiluted test material or 60 µl of test material diluted to 25% in mineral oil was applied as a single dose into a rubber chamber that had been previously affixed to the skin with epoxy and cyanoacrylate. A metal covering was placed on top of the chamber to prevent loss of test material. The animals were placed in metabolism chambers and urine and faeces were collected 24, 48, 72 and 96 hours after dosing. After 96 hours the animals were sacrificed and any unabsorbed test material was removed from the test site. The dosed area of skin was then removed from the carcass and processed for analysis of radiotracers. Samples of urine and faeces were also analysed for the presence of radiotracers. Percutaneous absorption was determined by summing the 14C activity in the urine, faeces and expired air and tissues.
Further groups of 5 males were used to assess the passive inhalation of labelled test material. This was accomplished by placing animals in metabolism chambers and collecting urine and faeces in a similar manner to that used for the dermally exposed animals. The labelled test material at the same doses as for the dermal study was placed in scintillation vials that were fixed to the inner wall of the metabolism chamber in a way that the animals could not come into contact with the vials.In the study with dermally applied undiluted test material approximately 5% of the labelled tetradecane and 15% of the labelled naphthalene was absorbed over 96 hours. In the study with the 25% concentration of test material, approximately 7% of the labelled tetradecane and 16% of the labelled naphthalene was absorbed over 96 hours. In the passive inhalation study approximately 2.8% (undiluted test material) and 1.8% (25% concentration) of the labelled naphthalene was bioavailable. In contrast, approximately 0.2% of labelled tetradecane in undiluted and diluted test material was absorbed.
These studies demonstrate that dilution of the test material in mineral oil did not influence absorption of the radiolabelled "spikes" present and that aromatics are absorbed better than saturates.
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