Not classified.
none
none
none
none
none
no data available
Fresh air, rest. Refer for medical attention.
Remove contaminated clothes. Rinse and then wash skin with water and soap.
First rinse with plenty of water for several minutes (remove contact lenses if easily possible), then refer for medical attention.
Rinse mouth. Rest. Refer for medical attention .
Inhalation of dust irritates nose and throat. Contact with eyes causes irritation. (USCG, 1999)
Immediate first aid: Ensure that adequate decontamination has been carried out. If patient is not breathing, start artificial respiration, preferably with a demand-valve resuscitator, bag-valve-mask device, or pocket mask, as trained. Perform CPR as necessary. Immediately flush contaminated eyes with gently flowing water. Do not induce vomiting. If vomiting occurs, lean patient forward or place on left side (head-down position, if possible) to maintain an open airway and prevent aspiration. Keep patient quiet and maintain normal body temperature. Obtain medical attention. Aromatic hydrocarbons and related compounds
To fight fire, use water, foam, carbon dioxide, water spray or mist, dry chemical.
This chemical is combustible. (NTP, 1992)
Use water spray, powder, foam, carbon dioxide. In case of fire: keep drums, etc., cool by spraying with water.
Sweep spilled substance into covered containers. Carefully collect remainder. Then store and dispose of according to local regulations. Do NOT let this chemical enter the environment. Personal protection: P2 filter respirator for harmful particles.
Sweep spilled substance into covered containers. Carefully collect remainder. Then store and dispose of according to local regulations. Do NOT let this chemical enter the environment. Personal protection: P2 filter respirator for harmful particles.
Collect and arrange disposal. Keep the chemical in suitable and closed containers for disposal. Remove all sources of ignition. Use spark-proof tools and explosion-proof equipment. Adhered or collected material should be promptly disposed of, in accordance with appropriate laws and regulations.
NO open flames. Closed system, dust explosion-proof electrical equipment and lighting. Prevent deposition of dust. Handling in a well ventilated place. Wear suitable protective clothing. Avoid contact with skin and eyes. Avoid formation of dust and aerosols. Use non-sparking tools. Prevent fire caused by electrostatic discharge steam.
Separated from strong oxidants. Well closed.Must be stored in places cool enough to prevent accidental ignition ... Provide adequate ventilation ... Locate storage area well away from areas of fire hazard ... Kept apart from powerful oxidizing agents ...
Component | Anthracene |
---|---|
CAS No. | 120-12-7 |
Recommended Exposure Limit: 10 Hr Time-Weighted Avg: 0.1 mg/cu m (cyclohexane-extractable fraction). /Coal tar pitch volatiles/ NIOSH considers coal tar pitch volatiles to be potential occupational carcinogens. /Coal tar pitch volatiles/ |
no data available
Ensure adequate ventilation. Handle in accordance with good industrial hygiene and safety practice. Set up emergency exits and the risk-elimination area.
Wear safety spectacles, face shield or eye protection in combination with breathing protection if powder.
Protective gloves.
Use ventilation (not if powder), local exhaust or breathing protection.
no data available
Solid. Flakes.
Light beige.
Weak aromatic odor
Ca. 213.9 °C. Atm. press.:Ca. 100 kPa.
342 °C. Atm. press.:1 013 hPa.
Combustible.
Lower flammable limit: 0.6% by volume; /No upper limit available/
Ca. 121 °C. Atm. press.:Ca. 101 kPa.
540 °C. Atm. press.:1 013 hPa.
no data available
no data available
no data available
less than 1 mg/mL at 68° F (NTP, 1992)
log Pow = Ca. 4.65. Temperature:20 °C.
0.001 Pa. Temperature:25 °C. Remarks:Standard?deviation:?+-0.2^-4?Pa.
Ca. 1.126 g/cm3. Temperature:20 °C.
6.15 (vs air)
no data available
80 mg/cu m; NIOSH considers coal tar pitch volatiles to be potential occupational carcinogens. Coal tar pitch volatiles
Decomposes on heating. Decomposes under the influence of strong oxidants. This produces acrid, toxic fume. This generates fire and explosion hazard.
Darkens in sunlight
COMBUSTIBLE WHEN EXPOSED TO HEAT, FLAME, OR OXIDIZING MATERIALS.Dust explosion possible if in powder or granular form, mixed with air.ANTHRACENE will spontaneously burst into flame on contact with chromic acid, and other strong oxidants.
no data available
Anthracene will burst into flame on contact with chromic acid.
Thermal decomposition products include carbon dioxide, carbon monoxide, and organic compounds. Aromatic hydrocarbons and related compounds
no data available
no data available
no data available
no data available
No data are available in humans. Inadequate evidence of carcinogenicity in animals. OVERALL EVALUATION: Group 3: The agent is not classifiable as to its carcinogenicity to humans.
no data available
The substance is mildly irritating to the skin and respiratory tract.
Repeated or prolonged contact with skin may cause dermatitis under the influence of UV light.
Evaporation at 20°C is negligible; a harmful concentration of airborne particles can, however, be reached quickly.
AEROBIC: The biodegradability of anthracene with natural sediments and natural esturine waters has been studied. The biodegradation of anthracene in aquatic media is controlled by the temperature, oxygen content and acclimatization or nonacclimatization of the microorganisms. Higher biodegradation rates were observed at 30 deg C than at 20 and 10 deg C. The biodegradation process was found to be aerobic and higher oxygen concentration up to a certain optimum value tended to increase the oxidation rates. Similarly, the biodegradation rates were reported to be faster with acclimatized microorganisms. The incubation of anthracene with intertidal sediment slurries for a reasonable period of time (approx 1 month) not only produces the mineralization product carbon dioxide but also produces intermediate metabolites A large portion of the initial material or its intermediate metabolites (which could not be identified because (14)carbon counting of the combustion products of residue was used as the method of quantification) remained cellular bound.
BCFs were measured in the following aquatic species: Goldfish, 162(1); Gambusia (fish), 1029(2); Rainbow trout, 4400 to 9200(3); Daphnia pulex, 759 to 912(4,5); Chlorella fusca variety vacuolata (green algae), 7760(6); Golden orfe, 912(7); Pontoporeia hoyi (scud), 17,000(8); and midge (Chironomousiparius), 46.7(9). A BCF of 7300 was measured in guppies, Poecilia reticulata, in static bioconcentration experiments(10). BCF values of 1660 to 2820 and 903 to 2710 were determined in carp using flow-through conditions and anthracene concns of 15 and 1.5 ug/L, respectively(11). According to a classification scheme(12), these BCFs suggest that bioconcentration in aquatic organisms ranges from moderate to very high(SRC). The BCF in Daphnia magna was found to decrease with increasing concn of Aldrich humic acids: BCF (dissolved organic carbon, mg/L), 607 (0.2) and 319 (2.0); however, this difference was not considered significant due to the large sample variance(13). Aldrich humic acids in water did not significantly alter Daphnia magna accumulation of anthracene: BCF (dissolved organic carbon, mg/L), 389 (0.3), 362 (1.5), and 340 (5.7)(13). Depuration half-lives of 57 and 63 hours relative to contaminated and clean water, respectively, were measured in Zebrafish, Brachydanio rerio, exposed to (14)C-labeled anthracene adsorbed on sediment(14).
The possibility of leaching of anthracene from soil to groundwater will depend on soil type. The Koc value for anthracene is 26,000. This indicates that anthracene will be adsorped strongly to soil and the compound may degrade before it reaches groundwater. Filtration of polluted surface water containing anthracene through sandy soil at a residence time of 100 days did not completely eliminate anthracene in the filtered water. The passage of anthracene through the soil was explained as a breakthrough of the chemical because of the saturation of active sorption sites.
no data available
The material can be disposed of by removal to a licensed chemical destruction plant or by controlled incineration with flue gas scrubbing. Do not contaminate water, foodstuffs, feed or seed by storage or disposal. Do not discharge to sewer systems.
Containers can be triply rinsed (or equivalent) and offered for recycling or reconditioning. Alternatively, the packaging can be punctured to make it unusable for other purposes and then be disposed of in a sanitary landfill. Controlled incineration with flue gas scrubbing is possible for combustible packaging materials.
ADR/RID: UN3077 (For reference only, please check.)
IMDG: UN3077 (For reference only, please check.)
IATA: UN3077 (For reference only, please check.)
ADR/RID: ENVIRONMENTALLY HAZARDOUS SUBSTANCE, SOLID, N.O.S. (For reference only, please check.)
IMDG: ENVIRONMENTALLY HAZARDOUS SUBSTANCE, SOLID, N.O.S. (For reference only, please check.)
IATA: ENVIRONMENTALLY HAZARDOUS SUBSTANCE, SOLID, N.O.S. (For reference only, please check.)
ADR/RID: 9 (For reference only, please check.)
IMDG: 9 (For reference only, please check.)
IATA: 9 (For reference only, please check.)
ADR/RID: III (For reference only, please check.)
IMDG: III (For reference only, please check.)
IATA: III (For reference only, please check.)
ADR/RID: Yes
IMDG: Yes
IATA: Yes
no data available
no data available