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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
Genetic toxicity: in vivo
Administrative data
- Endpoint:
- in vivo mammalian somatic cell study: cytogenicity / erythrocyte micronucleus
- Remarks:
- Type of genotoxicity: chromosome aberration
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Study period:
- August 20 – September 24, 1985
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- other: GLP study performed according to US EPA guidelines.
Data source
Reference
- Reference Type:
- study report
- Title:
- Unnamed
- Year:
- 1 985
- Report date:
- 1985
Materials and methods
Test guideline
- Qualifier:
- according to guideline
- Guideline:
- EPA OPP 84-2
- Deviations:
- no
- GLP compliance:
- yes
- Type of assay:
- micronucleus assay
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; 5601-56-1
- Substance type: Polycyclic aromatic hydrocarbon
- Physical state: White flake
- Analytical purity: Not provided
- Impurities (identity and concentrations): Not provided
- Lot/batch No.: #J-272
- Expiration date of the lot/batch: Not provided
- Stability under test conditions: Stipulated stable
- Storage condition of test material: Room temperature
Constituent 1
Test animals
- Species:
- mouse
- Strain:
- CD-1
- Sex:
- male/female
- Details on test animals or test system and environmental conditions:
- CD-1. Charles River Breeding Laboratory, Wilmington, MA
SOURCE:
- Age at study initiation: 8 ½ week
- Weight at study initiation: Males 28 – 35 g; females 26 – 29 g
- Fasting period before study: Not fasted
- Housing: 5 per cage per sex per dose group
- Diet (e.g. ad libitum): Wayne Rodent Blox, ad libitum
- Water (e.g. ad libitum): tap water, ad libitum
- Acclimation period: 5 days
ENVIRONMENTAL CONDITIONS – Definitive study
- Temperature (°C): 21 -22°C
- Humidity (%): 64 – 65%
- Air changes (per hr): not provided
- Photoperiod (hrs dark / hrs light): 12 hr dark /12 hr light
Administration / exposure
- Route of administration:
- intraperitoneal
- Vehicle:
- - Vehicle(s)/solvent(s) used: vegetable oil, Mazola corn oil
- Concentration of test material in vehicle: Range: 250,166.6, 150, 50, 25 mg/ml; Definitive 25 mg/ml
- Amount of vehicle (if gavage or dermal): 10 ml/kg
- Type and concentration of dispersant aid (if powder): None - Duration of treatment / exposure:
- Single injection
- Frequency of treatment:
- Once
- Post exposure period:
- 30, 48, 72 hours
- No. of animals per sex per dose:
- 5 per sex per dose
- Control animals:
- yes
- Positive control(s):
- - Control substance: triethylenemelamine, Lot # 25238, Polyscience, Inc., in 0.9% saline
- Route of administration: intraperitoneal
- Doses / concentrations: 0.5 mg/kg
Examinations
- Tissues and cell types examined:
- Bone marrow cells from femur
- Details of tissue and slide preparation:
- - CRITERIA FOR DOSE SELECTION: Range-finder
- TREATMENT AND SAMPLING TIMES (in addition to information in specific fields): 250 mg/kg sampled at 30, 48 and 72 hours
- DETAILS OF SLIDE PREPARATION: Cell suspension dropped on slide and stained with Giemsa
- METHOD OF ANALYSIS: Microscopic. 1000 PCE counted for presence of micronucleated PCE. Data expressed as number of micronucleated PCE versus total normal PCE per 1000 total PCE per animal. - Evaluation criteria:
- Micronuclei are uniform and darkly staining typically round bodies in the cytoplasm of PCE. Inclusions in PCEs which are reflective, improperly shaped or stained, or which are not in the focal plane of the cell are judged to be artefacts and are not scored as micronuclei. Cells containing more than one micronucleus are only scored once.
- Statistics:
- One-tailed “t” test to evaluate pairwise treatment groups with negative control. Statistical significance was judged at p< 0.05 and p< 0.01 levels.
Results and discussion
Test results
- Sex:
- male/female
- Genotoxicity:
- not determined
- Toxicity:
- yes
- Remarks:
- Signs of toxicity at 250 mg/kg.
- Vehicle controls validity:
- valid
- Negative controls validity:
- not examined
- Positive controls validity:
- valid
- Additional information on results:
- RESULTS OF RANGE-FINDING STUDY
- Dose range: 250 – 5000 mg/kg
- Solubility: 250 – 500mg/kg (25, 50 mg/ml)
- Clinical signs of toxicity in test animals: Decrease in body tone, abnormal gait, death at 500 mg/kg.
- Evidence of cytotoxicity in tissue analyzed: Not determined
- Rationale for exposure: 250 mg/kg determined to be the MTD
- Harvest times: 30, 48 and 72 hours
- High dose with and without activation: 250 mg/kg; activation not relevant
RESULTS OF DEFINITIVE STUDY
- Types of structural aberrations for significant dose levels (for Cytogenetic or SCE assay):
- Induction of micronuclei (for Micronucleus assay): None
- Ratio of PCE/NCE (for Micronucleus assay): Depression of PCE/NCE ratio at 72 hour sacrifice.
- Appropriateness of dose levels and route: Maximum tolerated dose (MTD)
- Statistical evaluation: “t” test negative
Any other information on results incl. tables
Animal Number |
Control |
Naphthalene (5601-56-1) |
|||
|
Corn Oil |
TEM |
250 mg/kg |
||
|
10 ml/kg |
0.5 mg/kg |
30 hours |
48 hours |
72 hours |
Male |
|||||
1 |
0 |
60 |
1 |
2 |
2 |
2 |
1 |
63 |
0 |
0 |
1 |
3 |
3 |
65 |
1 |
1 |
1 |
4 |
1 |
55 |
1 |
0 |
1 |
5 |
2 |
72 |
0 |
0 |
1 |
Female |
|||||
1 |
0 |
55 |
1 |
1 |
0 |
2 |
2 |
56 |
0 |
0 |
0 |
3 |
0 |
38 |
1 |
1 |
1 |
4 |
2 |
75 |
0 |
2 |
1 |
5 |
2 |
73 |
1 |
0 |
0 |
Mean |
1.30 ± 1.06 |
61.2 ± 11.09 |
0.60 ± 0.52 |
0.70 ± 0.82 |
0.80 ± 0.63 |
“t“ value |
-- |
16.997** |
1.878*a |
1.414 |
1.281 |
*, ** Denotes statistical significance at p<0.05 and 0.01 respectively
a Lower than control mean
Applicant's summary and conclusion
- Conclusions:
- Interpretation of results (migrated information): negative
Naphthalene is not a clastogen. - Executive summary:
In a preliminary dose-range finding study, naphthalene was administered intraperitoneally to 5 groups (2 males and 2 females per group) of CD-1 mice at dose levels of 250, 500, 1000, 3000, and 5000 mg/kg of body weight. Animals were observed for pharmacotoxic signs for up to 72 hours after dose administration. Pharmacotoxic signs were observed at all levels evaluated. All animals died at the 4 highest levels while animals at 250 mg/kg all survived treatment. Due to the severity of the signs and the mortality observed in the study, 250 mg/kg was selected as the dose for the Micronucleus Test as an estimate of the maximum tolerated dose. In the Micronucleus Test, three groups of ten animals (5 males and 5 females/group) were given single doses by intraperitoneal injection at 250 mg/kg and sacrificed at 30, 48, and 72 hours. Similar groups, dosed with the positive control, triethlyenemelamine (TEM), and negative control, corn oil, were evaluated concurrently. Slides were prepared from the bone marrow of the femurs and stained with Geimsa. Coded slides were scored for the number of polychromatic erythrocytes (PCE) with micronuclei in 1000 PCE per animal. The ratio of polychromatic to normochromatic erythrocytes per 1000 erythrocytes per animal was determined. The results for naphthalene were negative in the Micronucleus Test at a dose level of 250 mg/kg at all of the time intervals evaluated. These findings are based upon the inability of the test substance to produce a statistically significant increase in the number of micronuclei in 1000 polychromatic erythrocytes per animal in the treated groups versus the negative control group.
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