Registration Dossier
Registration Dossier
Data platform availability banner - registered substances factsheets
Please be aware that this old REACH registration data factsheet is no longer maintained; it remains frozen as of 19th May 2023.
The new ECHA CHEM database has been released by ECHA, and it now contains all REACH registration data. There are more details on the transition of ECHA's published data to ECHA CHEM here.
Diss Factsheets
Use of this information is subject to copyright laws and may require the permission of the owner of the information, as described in the ECHA Legal Notice.
EC number: 202-049-5 | CAS number: 91-20-3
- 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
Dermal absorption
Administrative data
- Endpoint:
- dermal absorption in vivo
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- other: Well performed study reported in detail, based on scientific principles, acceptable for assessment
Data source
Reference
- Reference Type:
- publication
- Title:
- A Comparative Study of the Kinetics and Bioavailability of Pure and Soil-Adsorbed Naphthalene in Dermally Exposed Male Rats
- Author:
- Turkall RM, Skowronski GA, Kadry AM, Abdel-Rahman MS
- Year:
- 1 994
- Bibliographic source:
- Arch. Environ. Contam. Toxicol. 26, 504-509 (1994)
Materials and methods
Test guideline
- Qualifier:
- equivalent or similar to guideline
- Guideline:
- OECD Guideline 427 (Skin Absorption: In Vivo Method)
- Deviations:
- not specified
- GLP compliance:
- not specified
Test material
- Reference substance name:
- Naphthalene
- EC Number:
- 202-049-5
- EC Name:
- Naphthalene
- Cas Number:
- 91-20-3
- Molecular formula:
- C10H8
- IUPAC Name:
- naphthalene
- Details on test material:
- - Name of test material (as cited in study report): Naphthalene (1,4,5,8-14C)
- Source: Custom synthesized by E.I. DuPont de Nemours and Co., Inc., New England Nuclear (NEN) Research Products (Boston, MA)
- Substance type: Organic, aromatic hydrocarbon
- Physical state: Solid
- Radiochemical purity (if radiolabelling): 99%.
- Specific activity (if radiolabelling): 15 mCi/mmol
- Locations of the label (if radiolabelling): C1,4,5 and 8
- Other: Prior to use, the radioisotope was diluted with pure ethyl alcohol, dehydrated U.S.P. (U.S. Industrial Chemicals Co., Division of National Distillers and Chemical Corp., NY) to reduce the specific activity to a workable range.
Constituent 1
- Radiolabelling:
- yes
Test animals
- Species:
- rat
- Strain:
- Sprague-Dawley
- Sex:
- male
- Details on test animals or test system and environmental conditions:
- TEST ANIMALS
- Source: Taconic Farms (Gerrnantown, NY)
- Weight at study initiation: 275-300 g
- Housing: Animals were housed three per cage
- Individual metabolism cages: yes
- Diet (e.g. ad libitum): Ralston Purina rodent lab chow (St. Louis, MO) ad libitum
- Water (e.g. ad libitum): Tap water ad libitum
- Acclimation period: at least 1 week
ENVIRONMENTAL CONDITIONS
- Temperature (°C): Constant temperature (23-25°C)
- Humidity (%): Constant and humidity (50-55%)
- Photoperiod (hrs dark / hrs light): 12 h light/dark cycle
Administration / exposure
- Type of coverage:
- occlusive
- Vehicle:
- ethanol
- Duration of exposure:
- 48 h
- Doses:
- 225 µl of an ethanol solution of 14C-naphthalene (5 µCi). The applied chemical dose was 3.3 µg naphthalene/cm2 skin surface area.
- No. of animals per group:
- five to eight
- Control animals:
- no
- Details on study design:
- A shallow glass cap (Q Glass Company, Towaco, N J) circumscribing a 13-cm2 area was tightly fixed with Lang's jet liquid acrylic and powder (Lang Dental Manufacturing Co., Inc, Chicago, IL) on the lightly shaved right costoabdominal region of each ether-anesthetised animal 0.5 hour prior to the administration of naphthalene. Care was taken to prevent any abrasion of the skin during shaving and cap attachment. The glass cap was attached immediately after shaving the animal and remained on the rat for the duration of the study. Then 225 µl of an ethanol solution of 14C-naphthalene (5 µCi) was introduced by syringe through a small opening in the cap which was immediately sealed. The applied chemical dose was 3.3 µg naphthalene/cm2 skin surface area.
In the absorption and elimination studies, each treatment group contained five to eight rats. Heparinised blood samples were collected by cardiac puncture under light ether anaesthesia at selected time points up to 48 h after treatment. Samples were processed, and radioactivity was measured by liquid scintillation spectrometry.
Groups of six rats each were administered pure naphthalene as described above. Animals were housed in all-glass metabolism chambers (Bio Serv Inc, Frenchtown, NJ) for the collection of expired air, urine, and faecal samples. Expired air was passed through activated charcoal tubes (SKC Inc., Eighty Four, PA) for the collection of the parent compound, then bubbled through traps filled with ethanolamine-ethylene glycol monomethyl ether (1:2, v/v) for the collection of 14CO2. All excreta were collected up to 48 h after administration of compound. Charcoal was extracted with toluene, while faecal samples were homogenised in deionised water. Aliquots of the charcoal extracts, ethanolamine-ethylene glycol monomethyl ether mixture, faecal homogenates, and urine were dispensed directly into Aquasol-2 (NEN) for analysis. At the conclusion of the excretion studies, whole blood was collected from the rats, after which they were sacrificed by an overdose of ether. Prior to removing the glass caps from the rats, the surface of the treated skin area was washed with ethyl alcohol to determine the percentage of radioactivity remaining on the skin application sites. Two to three mL of ethyl alcohol was introduced into the glass cap, and the animals were rotated from side to side. Aliquots of ethanol wash were removed from the skin and radioactivity counted. Glass caps were removed from the skin, and the following tissues excised and weighed: brain, thymus, thyroid, esophagus, stomach, duodenum, ileum, lung, pancreas, adrenal, testes, skin, fat, carcass, bone marrow, liver, kidney, spleen, and heart. Radioactivity was determined in the skin application site and in the untreated skin of the rat (left side). Three areas of fat were examined: namely, fat beneath treated or untreated skin and subrenal fat. Samples were processed, and radioactivity was quantitated as previously reported.
Results and discussion
- Signs and symptoms of toxicity:
- not examined
- Remarks:
- not relevant
- Dermal irritation:
- not examined
- Remarks:
- not relevant
- Absorption in different matrices:
- after 48 h:
- Skin test site
- Skin, untreated site:
- Blood:
- Urine: 70.3%
- Faeces: 3.7%
- Expired air (if applicable): 13.6% - Total recovery:
- - Total recovery: 87% after 48 hours
Percutaneous absorptionopen allclose all
- Dose:
- 43 µg
- Parameter:
- percentage
- Absorption:
- 87.6 %
- Remarks on result:
- other: 48 h
- Remarks:
- Basis for absorption is excretion during 48 hours after start of exposure
- Dose:
- 43 µg
- Parameter:
- percentage
- Absorption:
- 78 %
- Remarks on result:
- other: 24
- Remarks:
- Basis for absorption is excretion during 24 hours after start of exposure
- Conversion factor human vs. animal skin:
- not applicable
Any other information on results incl. tables
Plasma half-lives of radioactivity in male rats following dermal exposure to 14C-naphthalene were 2.1 h for absorption and 12.8 h for elimination. The major excretion route of radioactivity in male rats dermally exposed to naphthalene was via the urine. Approximately 50% of the radioisotope was recovered in the urine within 12 h of dosing. Another 20-25% of the dose was collected between 12 and 24 h (urinary excretion during the 0-24 h collection period 63%). Expired air was the secondary route of excretion (13.6% of the initial dose). The percentage of the administered dose expired as CO2 was less than 0.02%. Tissue distribution studies 48 h post-administration of naphthalene revealed that skin application sites contained the highest tissue concentrations of radioactivity with lesser concentrations determined in ileum, duodenum, and kidney. The major metabolite found in the urine of all naphthalene treated groups was 2,7-dihydroxynaphthalene followed by 1,2- dihydroxynaphthalene. Lower concentrations of 1,2-naphthoquinone, 1- and 2-naphthol, and two undetermined compounds were observed. Less than 0.5% of the parent compound was identified.
Applicant's summary and conclusion
- Conclusions:
- Results demonstrate that pure naphthalene applied dermally is absorbed relatively quickly into the plasma and is rapidly excreted into the urine.
- Executive summary:
Turkall et al. (1994) utilised pharmacokinetic techniques to assess the bioavailability of naphthalene following dermal
treatment of male Sprague Dawley rats. Animals were exposed to 43 µg total of 14C-naphthalene introduced into a shallow glass cap covering a 13-cm2 area on the skin of each rat. Plasma half-lives of radioactivity in male rats following dermal exposure to 14C-naphthalene were 2.1 h for absorption and 12.8 h for elimination. Plasma concentration reached a maximum 4 hours after start of exposure. The major excretion route of radioactivity in male rats dermally exposed to naphthalene was via the urine. Approximately 50% of the radioisotope was recovered in the urine within 12 h of dosing. Another 20-25% of the dose was collected between 12 and 24 h (urinary excretion during the 0-24 h collection period 63%). Expired air was the secondary route of excretion (13.6% of the initial dose). However, the percentage of the administered dose expired as CO2 was less than 0.02%. Tissue distribution studies 48 h post-administration of naphthalene revealed that skin application sites contained the highest tissue concentrations of radioactivity with lesser concentrations determined in ileum, duodenum, and kidney. The major metabolite found in the urine of all naphthalene treated groups was 2,7-dihydroxynaphthalene followed by 1,2- dihydroxynaphthalene. Lower concentrations of 1,2-naphthoquinone, 1- and 2-naphthol, and two undetermined compounds were observed. Less than 0.5% of the parent compound was identified.
Results demonstrate that pure naphthalene applied dermally absorbs relatively quickly into plasma. Naphthalene-derived radioactivity was rapidly excreted in urine. Between 70% and 87% of absorbed radioactivity was excreted as urinary metabolites, but another 6-14% was exhaled as parent compound.
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.