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EC number: 295-518-9 | CAS number: 92062-05-0 A complex combination of hydrocarbons obtained from the vacuum distillation of the products from a thermal cracking process. It consists predominantly of hydrocarbons having carbon numbers predominantly greater than C34 and boiling above approximately 495°C (923°F).
- 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 vitro / ex vivo
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Reliability:
- 2 (reliable with restrictions)
Data source
Reference
- Reference Type:
- publication
- Title:
- Percutaneous absorption of polycyclic aromatic compounds from bitumen fume condensate
- Author:
- Roy, T. A., Kriech, A. J. and Mackerer, C. R.
- Year:
- 2 007
- Bibliographic source:
- J. Occup. and Env. Hygiene, Volume 4, No. 81, Pages 137-143
Materials and methods
- Objective of study:
- absorption
Test guideline
- Qualifier:
- no guideline available
- Principles of method if other than guideline:
- Test material applied to sections of isolated human back skin mounted in a Franz diffusion cell. Dermal uptake was monitored by diffusion of material from the skin surface through to a receptor fluid.
Sections of human back skin were sliced with a dermatome to a thickness of ~250 µm, and 1-inch circular pieces were mounted in 6 Franz diffusion cells. Tissue integrity was assured by measurement of electrical resistance. Neat condensate was applied to the stratum corneum at "infinite dose" (200 µl) while the dermis was in direct contact with a receptor fluid vessel consisting of an aqueous solution of polyoxyethylene 20 oleyl ether.
Receptor fluids were sampled at 12 intervals over 48 hours, and analyzed by an HPLC system equipped with a variable wavelength detector and a fluorescence
detector connected in series. The UV detector was operated at 254 nm, and the fluorescence detector at ex630nm/em400nm, 18 nm bandpass.
The mobile phase was a 60-100% acetonitrile/water gradient.
Penetration rates of anthracene, fluoranthrene-pyrene, and total 3-6 ring polycyclic aromatic compounds (PAC) were measured. - GLP compliance:
- not specified
Test material
- Reference substance name:
- Asphalt, oxidized
- EC Number:
- 265-196-4
- EC Name:
- Asphalt, oxidized
- Cas Number:
- 64742-93-4
- IUPAC Name:
- Asphalt, oxidized
- Test material form:
- other: low viscosity liquid hydrocarbon
Constituent 1
- Radiolabelling:
- no
Test animals
- Species:
- human
- Sex:
- not specified
Administration / exposure
- Route of administration:
- dermal
- Vehicle:
- unchanged (no vehicle)
- Details on exposure:
- neat bitumen fume condensate (200ul) applied to the surface of skin samples (n=6) held in a Franz diffusion cell.
- Duration and frequency of treatment / exposure:
- Single application
Doses / concentrations
- Remarks:
- Doses / Concentrations:
200 ul
- No. of animals per sex per dose / concentration:
- 6 skin samples
- Control animals:
- no
- Details on study design:
- six skin samples used for the study. Aliquotes of the test material applied to the surface of skin samples mounted in Franz diffusion cells. The receptor fluid was sampled at 0, 2,4,8,12, 16, 20, 24, 30, 36 and 48 hrs after application and analysed for the presence of polycyclic aromatic hydrocarbon by HPLC.
- Details on dosing and sampling:
- test material applied (200 ul) using a positive displacemnt pipette.
Results and discussion
Toxicokinetic / pharmacokinetic studies
- Details on absorption:
- The rates of dermal penetration (ng/cm²/hr±SD) were:
anthracene 6.5 ± 0.9;
fluoranthene-pyrene 1.8 ± 0.3;
3-6 ring PAC 120 ± 30.
Percentages of applied dose absorbed were:
anthracene 5.3%,
fluoranthene-pyrene 3.3%,
3-6 ring PAC 1.8%.
The apparent permeability coefficient Kp (Kp = flux rate/applied concentration) for anthracene was 2 x 10-4 cm/hr.
Bioaccessibility (or Bioavailability)
- Bioaccessibility (or Bioavailability) testing results:
- These results demonstrate that dermal penetration of PAC, at low concentrations found in bitumen fume condensates can be measured by an
appropriately designed in vitro method.
Applicant's summary and conclusion
- Conclusions:
- Interpretation of results (migrated information): other: These results demonstrate that dermal penetration of PAC occurs, at low concentrations found in bitumen fume condensates.
Dermal penetration of PACs found in low concenetrations in bitumen fume condensate can occur. The amount amd rate of dermal uptake was relatively low. - Executive summary:
In an in-vitro dermal absorption study, 200 ul aliquots of neat bituen fume condensate, containing low concentrations of PACs, was applied to the surface of human skin samples fixed in a Franz Diffusion cell. Samples of the receptor fluid were analysed at time intervals ovr a 48hr period following application.
Results show that PACs present in bitumen fume condensate can penetrate the skin.
The rate of dermal flux (ng/cm²/hr±SD) for selected PACs was:
anthracene 6.5 ± 0.9; fluoranthene-pyrene 1.8 ± 0.3; whilst the rate for total 3-6 ring PAC was 120 ± 30.
The amount absorbed over a 48hr period was relatively low; measured values compared to aapplied dose were
anthracene 5.3%, fluoranthene-pyrene 3.3% and 3-6 ring PAC 1.8%.
The permeability coefficient Kp (Kp = flux rate/applied concentration) for anthracene was calculated to be 2 x 10-4 cm/hr.
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