Hazardous to the aquatic environment, short-term (Acute) - Category Acute 1
Hazardous to the aquatic environment, long-term (Chronic) - Category Chronic 1
H400 Very toxic to aquatic life
H410 Very toxic to aquatic life with long lasting effects
P273 Avoid release to the environment.
P391 Collect spillage.
none
P501 Dispose of contents/container to an appropriate treatment and disposal facility in accordance with applicable laws and regulations, and product characteristics at time of disposal.
no data available
Fresh air, rest.
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. Refer for medical attention .
Excerpt from ERG Guide 171 [Substances (Low to Moderate Hazard)]: Inhalation of material may be harmful. Contact may cause burns to skin and eyes. Inhalation of Asbestos dust may have a damaging effect on the lungs. Fire may produce irritating, corrosive and/or toxic gases. Some liquids produce vapors that may cause dizziness or suffocation. Runoff from fire control may cause pollution. (ERG, 2016)
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 if 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
Suitable extinguishing media: Use water spray, alcohol-resistant foam, dry chemical or carbon dioxide.[Sigma-Aldrich; Safety Data Sheet for Benzo
Excerpt from ERG Guide 171 [Substances (Low to Moderate Hazard)]: Some may burn but none ignite readily. Containers may explode when heated. Some may be transported hot. For UN3508, be aware of possible short circuiting as this product is transported in a charged state. (ERG, 2016)
In case of fire in the surroundings, use appropriate extinguishing media.
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.
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.
ACCIDENTAL RELEASE MEASURES: Personal precautions, protective equipment and emergency procedures: Avoid dust formation. Avoid breathing vapors, mist or gas. Ensure adequate ventilation. Environmental precautions: Prevent further leakage or spillage if safe to do so. Do not let product enter drains. Discharge into the environment must be avoided. Methods and materials for containment and cleaning up: Pick up and arrange disposal without creating dust. Sweep up and shovel. Keep in suitable, closed containers for disposal.[Sigma-Aldrich; Safety Data Sheet for Benzo
NO open flames. 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.
Well closed.Keep container tightly closed in a dry and well-ventilated place.[Sigma-Aldrich; Safety Data Sheet for Benzo
Component | Benzo[ghi]perylene |
---|---|
CAS No. | 191-24-2 |
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. NIOSH usually recommends that occupational exposures to carcinogens be limited to the lowest feasible concentration. /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 or eye protection in combination with breathing protection if powder.
Protective gloves. Protective clothing.
Use local exhaust or breathing protection.
no data available
Benzo[ghi]perylene is a colorless to white crystalline solid. Water insoluble.
Yellow-green fluorescent leaflets from benzene
no data available
273°C(lit.)
542°C(lit.)
Combustible under specific conditions.
no data available
36°C(lit.)
no data available
no data available
no data available
no data available
In water, 2.6X10-4 mg/L at 25 deg C
log Kow = 6.63
1.12E-09mmHg at 25°C
1.378g/cm3
no data available
no data available
NIOSH considers coal tar pitch volatiles to be potential occupational carcinogens. Coal tar pitch volatiles
Upon heating, toxic fumes are formed. Decomposes on heating. This produces toxic fumes.
Stable under recommended storage conditions.[Sigma-Aldrich; Safety Data Sheet for Benzo
Combustible under specific conditions.Vigorous reactions, sometimes amounting to explosions, can result from the contact between aromatic hydrocarbons, such as BENZO[GHI]PERYLENE, and strong oxidizing agents. They can react exothermically with bases and with diazo compounds. Substitution at the benzene nucleus occurs by halogenation (acid catalyst), nitration, sulfonation, and the Friedel-Crafts reaction.
no data available
Incompatible materials: Strong oxidizing agents.[Sigma-Aldrich; Safety Data Sheet for Benzo
Hazardous decomposition products formed under fire conditions - Carbon oxides.[Sigma-Aldrich; Safety Data Sheet for Benzo
no data available
no data available
no data available
no data available
CLASSIFICATION: D; not classifiable as to human carcinogenicity. BASIS FOR CLASSIFICATION: Based on no human data and inadequate animal data from lung implant, skin-painting and subcutaneous injection bioassays. HUMAN CARCINOGENICITY DATA: None. ANIMAL CARCINOGENICITY DATA: Inadequate.
no data available
no data available
no data available
Evaporation at 20°C is negligible; a harmful concentration of airborne particles can, however, be reached quickly.
AEROBIC: The half-life of benzo(ghi)perylene in Kidman sandy loam soil was determined to be 173 days (oil refinery waste on soil), 600 days (synthetic mixture on soil), and 863 days (1% creosote on soil)(1). After 5 weeks of incubation, benzo(ghi)perylene was approximately 18% degraded from a soil sample collected at a former manufactured gas plant site(2). A study in which polyaromatic hydrocarbon contaminated sludge was applied to 4 soil samples collected in Lancaster, England resulted in biodegradation half-lives of 460, 365, 460, and 535 days for benzo(ghi)perylene(3). A long term field study in which polyaromatic hydrocarbon contaminated sludge was applied to agricultural plots in England resulted in average biodegradation half-lives of 9.1 and 9.5 years for benzo(ghi)perylene(4). Eighty-one and 76% of an initial concentration of 9.96 ug/g benzo(ghi)perylene remained after 240 days in an unacclimated agricultural sandy loam soil incubated at 10 and 20 deg C, respectively; corresponding half-lives were estimated to be about 650 and 600 days(5). After 1,280 days, 78.3% of an initial concentration of benzo(ghi)perylene at 3.1 ug/g remained in a soil treated with oil sludge at a concentration of 17.0 ug/g(6). Biodegradation of PAHs having five or more rings, including benzo(ghi)perylene, was slight to non-existent in three soils under field conditions(7). Laboratory studies using sediment and water from the Yellow River, China, known to be contaminated with PAHs, found that biodegradation rates of benzo(ghi)perylene increased as the suspended sediment content of the water was increased(8); the bacteria population on the sediment was found to be far greater than in the water phase alone(8); a biodegradation rate approaching 50% was reached over a 30-day incubation period using the highest sediment contents(8).
An estimated BCF of 11,000 was calculated in fish for benzo(ghi)perylene(SRC), using a log Kow of 6.63(1) and a regression-derived equation(2). According to a classification scheme(3), this BCF suggests the potential for bioconcentration in aquatic organisms is very high(SRC), provided the compound is not metabolized by the organism(SRC). However, it may not bioconcentrate in aquatic organisms which contain microsomal oxidase, such as fish, as this enzyme enables the rapid metabolism of certain polycyclic aromatic hydrocarbons(4). A measured fish biotransformation half-life of 1.1 days has been reported for the analogous compound benzo(a)pyrene(5). Benzo(ghi)perylene was shown to bioaccumulate in worms exposed to contaminated sediment over a 4 week incubation period, reaching a maximum concentration of 80 ng/g(6).
A measured log Koc values of 6.80 (Koc of 6.3X10+6)(1) and 4.61 (Koc of 4.1X10+4)(2) have been reported for benzo(ghi)perylene. The Koc of benzo(ghi)perylene in 16 historically contaminated sediments ranged from 2.7X10+5 to 8.1X10+8 with a median of 1.3X10+7(3). According to a classification scheme(4), these Koc values suggest that benzo(ghi)perylene is expected to be immobile in soil. The log Kdoc (partition coefficient for sorption to dissolved organic carbon) of benzo(ghi)perylene was reported to range from 6.93 to 7.08; the log Kpoc (partition coefficient for sorption to particulate organic material was reported to be 6.8(5). The partition coefficient for sorption to dissolved organic carbon, Kdoc, of benzo(ghi)perylene to water-soluble soil organic matter in loam sand (from Newmarkt, Germany agriculture), clay loam (from Allersdorf, Germany forest), and humic acid (Aldrich) were determined to be 85710, 109570, and 614900, respectively(6).
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
Benzo(ghi)perylene is present as a component of polycyclic aromatic hydrocarbons (PAH) content in the environment usually resulting from the incomplete combustion or pyrolysis of organic matters, especially fossil fuels and tobacco.Data are insufficiently available on the effect of this substance on human health, therefore utmost care must be taken.