벤조니트릴

Excerpt from ERG Guide 152 [Substances - Toxic (Combustible)]:

Use powder, AFFF, foam, carbon dioxide. In case of fire: keep drums, etc., cool by spraying with water.

Fresh air, rest. Artificial respiration may be needed. Refer for medical attention.

Remove contaminated clothes. Rinse skin with plenty of water or shower. Refer for medical attention .

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 .

· CALL 911. Then call emergency response telephone number on shipping paper. If shipping paper not available or no answer, refer to appropriate telephone number listed on the inside back cover.

· ELIMINATE all ignition sources (no smoking, flares, sparks or flames) from immediate area.

EYES: First check the victim for contact lenses and remove if present. Flush victim's eyes with water or normal saline solution for 20 to 30 minutes while simultaneously calling a hospital or poison control center. Do not put any ointments, oils, or medication in the victim's eyes without specific instructions from a physician. IMMEDIATELY transport the victim after flushing eyes to a hospital even if no symptoms (such as redness or irritation) develop.

General First Aid:

Foam, dry chemical, carbon dioxide. Water may be ineffective. Cool exposed containers with water. Wear goggles & self-contained breathing apparatus.

If material on fire or involved in fire: Do not extinguish fire unless flow can be stopped. Use water in flooding quantities as fog. Solid streams of water may be ineffective. Cool all affected containers with flooding quantities of water. Apply water from as far a distance as possible. Use "alcohol" foam, dry chemical or carbon dioxide.

Evacuation: If fire becomes uncontrollable or container is exposed to direct flame, evacuate for a radius of 1500 feet. If material leaking (not on fire), downwind evacuation must be considered.

Suitable extinguishing media: Use water spray, alcohol-resistant foam, dry chemical or carbon dioxide.

For more Fire Fighting Procedures (Complete) data for BENZONITRILE (6 total), please visit the HSDB record page.

Conditions for safe storage, including any incompatibilities: Keep container tightly closed in a dry and well-ventilated place. Containers which are opened must be carefully resealed and kept upright to prevent leakage. Hygroscopic: Handle and store under inert gas.

Remove all ignition sources. Ventilate area of spill or leak. Absorb liquids in vermiculite, dry sand, earth, or a similar material adn deposit in sealed containers. it maybe nessary to contain and dispose of this chemical as a hazardous waste.

Accidental Release Measures. Personal precautions, protective equipment and emergency procedures: Use personal protective equipment. Avoid breathing vapours, mist or gas. Ensure adequate ventilation. Remove all sources of ignition. Beware of vapours accumulating to form explosive concentrations. Vapours can accumulate in low areas. 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: Contain spillage, and then collect with an electrically protected vacuum cleaner or by wet-brushing and place in container for disposal according to local regulations. Keep in suitable, closed containers for disposal.

SRP: The most favorable course of action is to use an alternative chemical product with less inherent propensity for occupational harm/injury/toxicity or environmental contamination. Recycle any unused portion of the material for its approved use or return it to the manufacturer or supplier. Ultimate disposal of the chemical must consider: the material's impact on air quality; potential migration in soil or water; effects on animal and plant life; and conformance with environmental and public health regulations.

Mix with calcium hypochlorite and flush to sewer with water or incinerate.

The following wastewater treatment technology has been investigated for benzonitrile: Concentration process: Biological treatment.

Waste treatment methods. Product: This combustible material may be burned in a chemical incinerator equipped with an afterburner and scrubber. Offer surplus and non-recyclable solutions to a licensed disposal company. Contact a licensed professional waste disposal service to dispose of this material. Contaminated packaging: Dispose of as unused product.

SRP: Wastewater from contaminant suppression, cleaning of protective clothing/equipment, or contaminated sites should be contained and evaluated for subject chemical or decomposition product concentrations. Concentrations shall be lower than applicable environmental discharge or disposal criteria. Alternatively, pretreatment and/or discharge to a permitted wastewater treatment facility is acceptable only after review by the governing authority and assurance that "pass through" violations will not occur. Due consideration shall be given to remediation worker exposure (inhalation, dermal and ingestion) as well as fate during treatment, transfer and disposal. If it is not practicable to manage the chemical in this fashion, it must be evaluated in accordance with EPA 40 CFR Part 261, specifically Subpart B, in order to determine the appropriate local, state and federal requirements for disposal.

Benzonitrile was qualitatively detected in 3 of 12 samples of human milk collected from volunteers in Bayonne, NJ, Jersey City, NJ, Bridgeville, PA, and Baton Rouge, LA(1). Benzonitrile was detected in 24.6% of 387 of expired air samples collected from healthy, urban human adults; the mean concentration in expired air was 0.105 ng/L(2).

Antidotes to cyanide poisoning include hydroxocobalamin and sodium nitrite, which release the cyanide from the cytochrome system, and rhodanase, which is an enzyme occurring naturally in mammals that combines serum cyanide with thiosulfate, producing comparatively harmless thiocyanate. Oxygen therapy can also be administered. (L97)

Benzonitrile was tested for anticonvulsant effect in mice and gave protection against pentylenetetrazole-induced convulsions.

The extent of cyanide liberation and the effect of carbon tetrachloride pretreatment on the mortality of /mice/ differed among nitriles. Benzonitrile toxicity was clearly enhanced.

When sodium thiosulfate was given in multiple injections, it protected mice against death by propionitrile.

The toxic mechanism of nitriles and the effect of metabolic modifiers in mice were studied in relation to their physicochemical properties. All the test nitriles liberated cyanide both in vivo and in vitro, with the exception of benzonitrile, although the extent of liberation and the effect of carbon tetrachloride pretreatment on the mortality of animals differed among nitriles. From these results, test compounds were tentatively divided into 3 groups. In group 1, acute toxicity was greatly reduced by carbon tetrachloride pretreatment, in group 2, toxicity was not significantly changed or was somewhat enhanced, and in group 3, benzonitrile only, toxicity was clearly enhanced. The amount of cyanide was higher at death in the brains of mice given group 1 compounds, the level being comparable to that found in mice killed by dosing with potassium cyanide. The relation between log (1/LD50) and log p for the compounds in group 1 fitted a parabolic plot, while that for compounds in group 2 was linear. For most nitriles, the in vitro metabolism was inhibited when the incubation mixture contained either SKF-525A, carbon monoxide, or microsomes from mice treated with carbon tetrachloride. When mice were dosed with ethyl alcohol, metabolic enhancement of nitriles was seen compared with the control. However, ethyl alcohol, when added to the incubation mixture, inhibited the in vitro metabolism of nitriles. /Nitriles/

Exposure to high levels of cyanide for a short time harms the brain and heart and can even cause coma, seizures, apnea, cardiac arrest and death. Chronic inhalation of cyanide causes breathing difficulties, chest pain, vomiting, blood changes, headaches, and enlargement of the thyroid gland. Skin contact with cyanide salts can irritate and produce sores. (L96, L97)

EC50; Species: Daphnia magna (Water Flea) age < or =24 hr; Conditions: freshwater, static, 20-22 °C, pH 7.6-7.7; Concentration: 200000 ug/L for 24 hr; Effect: intoxication, immobilization /formulation/

LC50; Species: Oryzias latipes (Japanese Medaka) length 2 cm, weight 0.2 g; Conditions: freshwater, static, 25 °C; Concentration: 27000 ug/L for 24 hr

LC50; Species: Oryzias latipes (Japanese Medaka) length 2 cm, weight 0.2 g; Conditions: freshwater, static, 25 °C; Concentration: 15000 ug/L for 48 hr

TERRESTRIAL FATE: Based on a classification scheme(1), an estimated Koc value of 150(SRC), determined from a log Kow of 1.56(2) and a regression-derived equation(3), indicates that benzonitrile is expected to have moderate mobility in soil(SRC). Volatilization of benzonitrile from moist soil surfaces is expected to be an important fate process(SRC) given an estimated Henry's Law constant of 5.21X10-5 atm-cu m/mole (SRC), derived from its vapor pressure, 0.768 mm Hg(4), and water solubility of 2000 mg/L(5). Benzonitrile is not expected to volatilize from dry soil surfaces(SRC) based upon its vapor pressure(4). Benzonitrile achieved 88% degradation after 8, 10, and 12.5 hours in char-amended soil, soil and washed-char-amended soil slurries, respectively(6), indicating that biodegradation may be an important environmental fate process in soil(SRC).

AQUATIC FATE: Based on a classification scheme(1), an estimated Koc value of 150(SRC), determined from a log Kow of 1.56(2) and a regression-derived equation(3), indicates that benzonitrile is not expected to adsorb to suspended solids and sediment(SRC). Volatilization from water surfaces is expected(4) based upon an estimated Henry's Law constant of 5.21X10-5 atm-cu m/mole(SRC), derived from its vapor pressure, 0.768 mm Hg(5), and water solubility of 2000 mg/L(6). Using this Henry's Law constant and an estimation method(4), volatilization half-lives for a model river and model lake are 20 and 9 days, respectively(SRC). According to a classification scheme(7), an estimated BCF of 5(SRC), from its log Kow(2) and a regression-derived equation(3), suggests the potential for bioconcentration in aquatic organisms is low(SRC). Utilizing the Japanese MITI test, 63% of the Theoretical BOD was reached in 2 weeks(8) indicating that biodegradation is an important environmental fate process in water(SRC).

ATMOSPHERIC FATE: According to a model of gas/particle partitioning of semivolatile organic compounds in the atmosphere(1), benzonitrile, which has a measured vapor pressure of 0.768 mm Hg at 25 °C(2), is expected to exist solely as a vapor in the ambient atmosphere(SRC). Vapor-phase benzonitrile is degraded in the atmosphere by reaction with photochemically-produced hydroxyl radicals(SRC); the half-life for this reaction in air is estimated to be 31 days(SRC), calculated from its rate constant of 3.30X10-13 cu cm/molecule-sec at 25 °C(3). Benzonitrile absorbs light at wavelengths >290 nm(4) and, therefore, may be susceptible to direct photolysis by sunlight(SRC).

Benzonitrile was qualitatively detected in the volatile components of baked potatoes(1), roasted filbert nuts(2), chickpeas(3), and meat(4).

Benzonitrile is found in milk products, roasted filberts and peanuts, and cooked trassi.

The substance can be absorbed into the body by inhalation, through the skin and by ingestion.

Oral (L96) ; inhalation (L96) ; dermal (L96)

Benzonitrile was qualitatively detected in 3 of 12 samples of human milk collected from volunteers in Bayonne, NJ, Jersey City, NJ, Bridgeville, PA, and Baton Rouge, LA(1).

Benzonitrile is found in milk products.

IDENTIFICATION AND USE: Benzonitrile is a colorless liquid. It is used as intermediate for rubber chemicals; solvent for nitrile rubber, specialty lacquers, and many resins and polymers, and for many anhydrous metallic salts. HUMAN EXPOSURE AND TOXICITY: Benzonitrile was tested at a concentration of 2% in petrolatum on 27 volunteers in a mixed panel, and was found to produce no sensitization reactions after 48 hr close patch test. Extensive reddening and blister formation resulted from accidental exposure of human skin to benzonitrile. Following an occupational accident in which a worker's head and clothing were drenched with benzonitrile, the worker suffered severe respiratory distress and tonic convulsions between periods of unconsciousness which lasted for 75 min. Thereafter he gradually recovered, but several years later he experienced episodes of unconsciousness which might have been related to the benzonitrile exposure. ANIMAL STUDIES: CNS depression signs and changes in blood cholinesterase activity were observed in rats and mice in an inhalation study with benzonitrile. Indication of cumulative effects of benzonitrile were reported. Toxic signs included sluggishness, unsteady gait, a comatose state, convulsions of limb muscles, and death. Benzonitrile produced mild eye irritation and no skin irriation in albino rabbits. Benzonitrile applied full strength to intact or abraded rabbit skin for 24 hr under occlusion was moderately irritating. When benzonitrile was administered orally to rats in a single lethal dose (2 g/kg), cytochrome oxidase activity of the liver, kidneys, and heart was increased by 2-4 times. The nitrile initially increased the hippuric acid and NH3 and decreased the glucuronides of the urine. Rhodanides in the blood remained unchanged. Certain responses of rats following exposure to benzonitrile vapor exhibited age-rated differences. Erythrocyte and leukocyte counts and hemoglobin , albumin and gamma-globulin levels decreased while alpha1-, alpha2- and beta-globulin levels increased earlier and were compensated far more rapidly in adult rats than in juvenile or older animals. Both, nitrobenzene and benzonitrile applied to V79 cells, induced mostly kinetochor (CREST)-positive micronuclei, thus characterising the chromosomal effects as aneugenic. Benzonitrile was tested for anticonvulsant effect in mice and gave protection against pentylenetetrazole-induced convulsions.

Organic nitriles decompose into cyanide ions both in vivo and in vitro. Consequently the primary mechanism of toxicity for organic nitriles is their production of toxic cyanide ions or hydrogen cyanide. Cyanide is an inhibitor of cytochrome c oxidase in the fourth complex of the electron transport chain (found in the membrane of the mitochondria of eukaryotic cells). It complexes with the ferric iron atom in this enzyme. The binding of cyanide to this cytochrome prevents transport of electrons from cytochrome c oxidase to oxygen. As a result, the electron transport chain is disrupted and the cell can no longer aerobically produce ATP for energy. Tissues that mainly depend on aerobic respiration, such as the central nervous system and the heart, are particularly affected. Cyanide is also known produce some of its toxic effects by binding to catalase, glutathione peroxidase, methemoglobin, hydroxocobalamin, phosphatase, tyrosinase, ascorbic acid oxidase, xanthine oxidase, succinic dehydrogenase, and Cu/Zn superoxide dismutase. Cyanide binds to the ferric ion of methemoglobin to form inactive cyanmethemoglobin. (L97)

Confusion. Headache. Laboured breathing. Nausea. Unconsciousness. Vomiting. Weakness.

Redness.

Redness. Pain.

Further see Inhalation.

Cyanide poisoning is identified by rapid, deep breathing and shortness of breath, general weakness, giddiness, headaches, vertigo, confusion, convulsions/seizures and eventually loss of consciousness. (L96, L97)

This action promulgates standards of performance for equipment leaks of Volatile Organic Compounds (VOC) in the Synthetic Organic Chemical Manufacturing Industry (SOCMI). The intended effect of these standards is to require all newly constructed, modified, and reconstructed SOCMI process units to use the best demonstrated system of continuous emission reduction for equipment leaks of VOC, considering costs, non air quality health and environmental impact and energy requirements. Benzonitrile is produced, as an intermediate or a final product, by process units covered under this subpart.

Persons in charge of vessels or facilities are required to notify the National Response Center (NRC) immediately, when there is a release of this designated hazardous substance, in an amount equal to or greater than its reportable quantity of 5000 lb or 2270 kg. The toll free number of the NRC is (800) 424-8802. The rule for determining when notification is required is stated in 40 CFR 302.4 (section IV. D.3.b).

Benzonitrile is designated as a hazardous substance under section 311(b)(2)(A) of the Federal Water Pollution Control Act and further regulated by the Clean Water Act Amendments of 1977 and 1978. These regulations apply to discharges of this substance. This designation includes any isomers and hydrates, as well as any solutions and mixtures containing this substance.