アセトニトリル

Excerpt from ERG Guide 127 [Flammable Liquids (Water-Miscible)]:

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

Fresh air, rest. Artificial respiration may be needed. No mouth-to-mouth artificial respiration. Refer immediately for medical attention.

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

Rinse with plenty of water (remove contact lenses if easily possible). Refer immediately for medical attention.

Rinse mouth. Give one or two glasses of water to drink. Do NOT induce vomiting. Refer immediately 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:

(General first aid procedures)

VAPOR HEAVIER THAN AIR & MAY TRAVEL CONSIDERABLE DISTANCE TO SOURCE OF IGNITION & FLASH BACK.

Vapors are heavier than air and may travel to a source of ignition and flash back.

· Wear positive pressure self-contained breathing apparatus (SCBA).

10.0 [ppm]

Foam, carbon dioxide, dry chemical

Stay upwind and use water spray to knock down vapor.

Approach fire from upwind to avoid hazardous vapors and toxic decomposition products. Use water spray, dry chemical, "alcohol resistant" foam, or carbon dioxide. Use water spray to keep fire-exposed containers cool.

Advice for firefighters: wear self contained breathing apparatus for fire fighting if necessary.

For more Fire Fighting Procedures (Complete) data for ACETONITRILE (7 total), please visit the HSDB record page.

Protect containers against physical damage. Outdoor or detached storage is preferable. Separate from any sources of ignition and combustible materials. Storage room should be well-ventilated.

Inside storage should be in a standard flammable liquids storage warehouse, room, or cabinet. Separate from oxidizing materials. Outside or detached storage is preferred.

Store in tightly closed containers in a cool, well ventialted area. Metal containers involving the transfer of this chemical should be grounded and bonded. Where possible, automatically pump liquid from drums or other storage containers to process containers. Drums must be equipped with self-closing valves, pressure vacuum bungs; and flame arresters. Use only non-sparking tools and equipment, especially when opening and closing containers of this chemical.

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. Evacuate personnel to safe areas. 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.; 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.

Restrict persons not wearing protective equipment from area of spill or leak until cleanup is complete. Remove all ignition sources. Establish forced ventilation to keep levels below explosive limit. Use foam spray to reduce vapors. Absorb liquids in vermiculite, dry sand, earth, or a similar material and deposit in sealed containers. Keep acetonitrile out of a confined space, such as a sewer, because of the potential for an explosion, unless the sewer is designed to prevent the build-up of explosive concetrations. It may be necessary to contain and dispose of this chemical as a hazardous waste. If material or contaminated runoff enters waterways, notify downstream users of potentially contaminated waters. Contact your Department of Environmental Protection or your regional office of the federal EPA for specific recommendations. If employees are required to clean-up spills, they must be properly trained and equipped.

1) Remove all ignition sources. 2) Ventilate area of spill or leak. 3) For small quantities, absorb on paper towels. Evaporate in safe place (such as fume hood). Allow ... vapors to completely clear ductwork. Burn paper in suitable location away from combustible materials. Large quantities can be collected & atomized in suitable combustion chamber equipped with appropriate effluent gas cleaning device. ... /It/ should not be allowed to enter confined space, such as sewer ...

Eliminate all ignition sources. Approach release from upwind. Stop or control the leak, if this can be done without undue risk. Use water spray to cool and disperse vapors, protect personnel, and dilute spills to form nonflammable mixtures. Control runoff and isolate discharged material for proper disposal.

For more Cleanup Methods (Complete) data for ACETONITRILE (6 total), please visit the HSDB record page.

Generators of waste (equal to or greater than 100 kg/mo) containing this contaminant, EPA hazardous waste number U003, must conform with USEPA regulations in storage, transportation, treatment and disposal of waste.

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.

Consult with environmental regulatory agencies for guidance on acceptable disposal practices. Generators of waste containing this contaminant (>/= 100 kg/mo) must conform with EPA regulations governing storage, transportation, treatment, and waste disposal. Incineration with nitrogen oxide removal from effluent gases by scrubbers or incinerators.

Acetonitrile is a waste chemical stream constituent which may be subjected to ultimate disposal by controlled incineration. Oxides of nitrogen are removed from the effluent gas by scrubbers and/or thermal devices.

For more Disposal Methods (Complete) data for ACETONITRILE (7 total), please visit the HSDB record page.

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)

The purpose of these studies was to investigate the nature and mechanism of a toxicologic interaction between acetonitrile and acetone. Results of oral dose-response studies utilizing a 1:1 (w/w) mixture of acetonitrile and acetone, or varying doses of acetonitrile administered together with a constant dose of acetone, indicated that acetone potentiated acute acetonitrile toxicity three- to fourfold in rats. The onset of severe toxicity (manifested by tremors and convulsions) was delayed in the groups dosed with both solvents compared to the groups that received acetonitrile or acetone alone. Blood cyanide (a metabolite of acetonitrile) and serum acetonitrile and acetone concentrations were measured after oral administration of 25% aqueous solutions of acetonitrile, acetone, or acetonitrile plus acetone. Concentrations of cyanide in the blood of rats given acetonitrile plus acetone remained near baseline, in contrast to the high concentrations found in rats dosed with acetonitrile alone. At 34-36 hr, high blood cyanide concentrations were found in rats dosed with both of the solvents. This delayed onset of elevation of blood cyanide coincided with the occurrence of clinical signs and with the disappearance of serum acetone. In further pharmacokinetic studies, blood cyanide concentrations were measured after similar dosage regimens of acetone and acetonitrile. Peak cyanide concentrations were found to be significantly greater in rats dosed with both solvents than in rats given only acetonitrile. Administration of either sodium thiosulfate or a second dose of acetone prevented the toxicity associated with exposure to both solvents. These results suggest that the effects of acetone on acetonitrile toxicity are due to a biphasic effect on the metabolism of acetonitrile to cyanide, that is, an initial inhibition followed by a stimulation of this metabolism upon acetone elimination.

The effect of ethanol on the metabolism of 20 nitriles was studied in vivo and in vitro in mice. At 13 hr after ethanol dosing (4.0 g/kg), the metabolism of acetonitrile by isolated hepatic microsomes was 1.83 times controls (ie, glucose).

Male CD-1 mice were exposed for 60 min to toxic concentrations of acetonitrile, propionitrile, or n-butyronitrile and were maintained for the following 14 days. The LC50 values for acetonitrile, propionitrile, and n-butyronitrile were 2,693, 163, and 249 ppm, respectively. Pretreatment with Na2S2O3 /(sodium thiosulfate)/ or NaNO2 /(sodium nitrite)/, two common inorganic cyanide antagonists, can provide significant (p<0.05) protection against the mortality associated with exposure to lethal concentrations of these nitriles. Administration of Na2S2O3 consistently provided a greater measure of protection than did NaNO2 against nitrile poisoning. Pretreatment with a heptatotoxic dose of CCl4 can protect mice against death from inhalation of lethal concentrations of these nitriles.

...rabbits injected with acetonitrile excreted 27-35% of the dose as thiocyanate, while in thyroid-ectomized rabbits, the excretion decreased significantly (3-5% of the dose). Thiocyanate excretion increased notably upon feeding dessicated thyroid to these animals.

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)

LC50; Species: Pimephales promelas (fathead minnow); Concentration: 1020 mg/L for 96 hr (hard water) /Conditions of bioassay not specified/

LC50; Species: Pimephales promelas (fathead minnow); Concentration: 1000 mg/L for 96 hr (soft water) /Conditions of bioassay not specified/

LC50; Species: Lepomis macrochirus (bluegill); Concentration: 1850 mg/L for 96 hr (soft water) /Conditions of bioassay not specified/

LC50; Species: Lebistes reticulatus (guppy); Concentration: 1650 mg/L for 96 hr (soft water) /Conditions of bioassay not specified/

For more Ecotoxicity Values (Complete) data for ACETONITRILE (25 total), please visit the HSDB record page.

TERRESTRIAL FATE: Based on a classification scheme(1), a Koc value of 2.2(2) indicates that acetonitrile is expected to have very high mobility in soil(SRC). Volatilization of acetonitrile from moist soil surfaces is expected to be an important fate process(SRC) given a Henry's Law constant of 3.45X10-5 atm-cu m/mole(3). Acetonitrile is expected to volatilize from dry soil surfaces(SRC) based upon a vapor pressure of 88.8 mm Hg(4). A 65% of theoretical BOD using activated sludge in the Japanese MITI test(5) suggests that biodegradation may be an important environmental fate process in soil(SRC). Available screening studies suggest that acetonitrile is readily biodegradable by adapted microbial populations(6). Biodegradation is generally slower with non-adapted microbes(7,8).

AQUATIC FATE: Based on a classification scheme(1), a Koc value of 2.2(2) indicates that acetonitrile is not expected to adsorb to suspended solids and sediment(SRC). Volatilization from water surfaces is expected(3) based upon a Henry's Law constant of 3.45X10-5 atm-cu m/mole(4). Using this Henry's Law constant and an estimation method(3), volatilization half-lives for a model river and model lake are 12 hours and 7.5 days, respectively(SRC). According to a classification scheme(5), an estimated BCF of 3(SRC), from its log Kow of -0.34(6) and a regression-derived equation(7), suggests the potential for bioconcentration in aquatic organisms is low(SRC). A 65% of theoretical BOD using activated sludge in the Japanese MITI test(8) suggests that biodegradation might be an important environmental fate process in soil(SRC). Available screening studies suggest that acetonitrile is readily biodegradable by adapted microbial populations(9). Biodegradation is generally slower with non-adapted microbes(10,11). The biodegradability of acetonitrile in river water had an observed 12-day ThOD (theoretical oxygen demand) of 40%(12,13). In acclimated river water, 100% removal was observed after 4 days(9). Chemical hydrolysis in water is not expected to be an important fate process(SRC) since the hydrolysis half-life at pH 7 (25 °C) is reported to be >150,000 years(14).

ATMOSPHERIC FATE: According to a model of gas/particle partitioning of semivolatile organic compounds in the atmosphere(1), acetonitrile, which has a vapor pressure of 88.8 mm Hg at 25 °C(2), is expected to exist solely as a vapor in the ambient atmosphere. Vapor-phase acetonitrile 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 610 days(SRC), calculated from its rate constant of 2.63X10-14 cu cm/molecule-sec at 25 °C(3). Vapor-phase acetonitrile is also degraded in the atmosphere by reaction with ozone(SRC); the half-life for this reaction in air is estimated to be greater than or equal to 76 days(SRC), calculated from its rate constant of less than or equal to 1.5X10-19 cu cm/molecule-sec at 25 °C(4). Direct photolysis of acetonitrile in the atmosphere is not expected to be an important fate process(4) since acetonitrile absorbs light only in the far UV region(5) with a UV maximum below 160 nm(4). The removal of acetonitrile from the atmosphere by precipitation has been reported to be an important fate process(4).

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

inhalation, skin absorption, ingestion, skin and/or eye contact

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

Acetonitrile was detected in 35 surveyed samples of cow milk at concentrations ranging from 1.51 to 13.75 ng/mL (whole), 4.00 to 12.51 ng/mL (2% butterfat), and 4.03 to 12.74 ng/mL (1% butterfat). Average detected concentrations were 7.56 ng/mL (whole), 8.98 ng/mL (2% butterfat), and 7.10 ng/mL (1% butterfat). The samples represented 8 brands of pasteurized milk in Las Vegas, Nevada between January 2002 and February 2002(1).

IDENTIFICATION AND USE: Acetonitrile is a liquid with an ether like odor. It is a volatile highly polar solvent used in many different industrial applications including use for the hydrocarbon extraction processes, especially for butadiene; intermediate; catalyst; separation of fatty acids from vegetable oils; and manufacturing of synthetic pharmaceuticals. It is also the starting material for many types of nitrogen-containing compounds, It can be metabolized to produce hydrogen cyanide, which is the source of the observed toxic effects. HUMAN EXPOSURE AND TOXICITY: Symptoms and signs of acute acetonitrile intoxication include chest pain, tightness in the chest, nausea, emesis, tachycardia, hypotension, short and shallow respiration, headache, restlessness and seizures. The systemic effects appear to be attributable to the conversion of acetonitrile to cyanide. Blood cyanide and thiocyanate levels are elevated during acute intoxication. Fatalities after exposure to acetonitrile in the workplace and fatal cases of a child ingesting an acetonitrile containing cosmetic have been reported. Elevated tissue cyanide concentrations were found in postmortem examination of these cases. Acetonitrile is readily absorbed from the gastrointestinal tract, through the skin and the lungs. All three routes of exposure have been reported to lead to systemic effects. No epidemiological study of cancer incidence could be located. ANIMAL STUDIES: There are substantial data to suggest that most of the systemic toxic effects of acetonitrile are mediated through its metabolism to cyanide, which is catalyzed by the cytochrome P450 monooxygenase system. Cyanide is subsequently conjugated with thiosulfate to form thiocyanate which is eliminated in the urine. Peak concentrations of cyanide in the blood of rats following administration of near lethal doses of acetonitrile approximate concentrations observed following the administration of a lethal dose of potassium cyanide. The peak concentration of cyanide after administration of acetonitrile is delayed by up to several hours as compared to other nitriles. The more rapid rate at which cyanide is produced in the mouse appears to account for the much greater sensitivity of this species to the toxic effects of acetonitrile. A portion of the acetonitrile is also eliminated unchanged in expired air and in the urine. Guinea pigs are also another sensitive species to acetonitrile intoxication. The main symptoms in animals appear to be prostration followed by seizures. Dermal application of acetonitrile causes systemic toxicity in animals. Rats were given gavage doses of 125, 190, or 275 mg acetonitrile/kg from gestational days 6 through 19. An increase in post-implantation loss, with a decrease in viable fetuses, was seen at 275 mg/kg. There were no structural abnormalities in the fetuses derived from acetonitrile-exposed rats. Developmental study in pregnant Syrian golden hamsters exposed up to 8,000 ppm acetonitrile for 1 hour on gestational day 8 and then sacrificed on gestational day 14 demonstrated maternal toxixity and fetotoxicity. Abnormal fetuses exhibiting exencephaly and rib fusions were recovered; surviving litters at 8,000 ppm developed severe axial skeletal dysraphic disorders; one 8,000-ppm fetus exhibited extrathoracic ectopia cordis with accompanying defects in the sternum of the heart. Acetonitrile was not mutagenic in Salmonella typhimurium strain TA97, TA98, TA100, TA1535, or TA1537, with or without metabolic activation. In cultured Chinese hamster ovary cells, acetonitrile produced a weakly positive response in the sister chromatid exchange test without, but not with metabolic activation. A small increase in chromosomal aberrations was observed in cultured Chinese hamster ovary cells treated with acetonitrile in the presence, but not in the absence, of metabolic activation. A significant increase in micronucleated normochromatic erythrocytes was observed in peripheral blood samples from male mice treated with acetonitrile for 13 weeks; the frequency of micronucleated erythrocytes in female mice was not affected by exposure to acetonitrile.

U003; As stipulated in 40 CFR 261.33, when acetonitrile, as a commercial chemical product or manufacturing chemical intermediate or an off-specification commercial chemical product or a manufacturing chemical intermediate, becomes a waste, it must be managed according to Federal and/or State hazardous waste regulations. Also defined as a hazardous waste is any residue, contaminated soil, water, or other debris resulting from the cleanup of a spill, into water or on dry land, of this waste. Generators of small quantities of this waste may qualify for partial exclusion from hazardous waste regulations (40 CFR 261.5).

Pursuant to section 8(d) of TSCA, EPA promulgated a model Health and Safety Data Reporting Rule. The section 8(d) model rule requires manufacturers, importers, and processors of listed chemical substances and mixtures to submit to EPA copies and lists of unpublished health and safety studies. Acetonitrile is included on this list. Effective date: 10/4/82; Sunset date: 10/4/92.

Section 8(a) of TSCA requires manufacturers of this chemical substance to report preliminary assessment information concerned with production, exposure, and use to EPA as cited in the preamble in 51 FR 41329. Effective date: 8/4/95; Reporting date: 10/3/95.

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. Acetonitrile is produced, as an intermediate or a final product, by process units covered under this subpart.

Listed as a hazardous air pollutant (HAP) generally known or suspected to cause serious health problems. The Clean Air Act, as amended in 1990, directs EPA to set standards requiring major sources to sharply reduce routine emissions of toxic pollutants. EPA is required to establish and phase in specific performance based standards for all air emission sources that emit one or more of the listed pollutants. Acetonitrile is included on this list.

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).

Acetonitrile is predominantly used as a solvent in the manufacture of pharmaceuticals, for spinning fibers and for casting and molding of plastic materials, in lithium batteries, for the extraction of fatty acids from animal and vegetable oils, and in chemical laboratories for the detection of materials such as pesticide residues.

Used as a solvent for extraction of hydrocarbons, for separation of fatty acids from vegetable oils, and as a specialty solvent; [ACGIH]

Semiconductor Manufacturing [Category: Industry]

Smoking cigarettes [Category: Food & Drugs]

Solvent in hydrocarbon extraction processes, especially for butadiene; specialty solvent; intermediate; catalyst; separation of fatty acids from vegetable oils; manufacturing of synthetic pharmaceuticals.

In organic synthesis as starting material for acetophenone, alpha-naphthaleneacetic acid, thiamine, acetamidine. To remove tars, phenols, and coloring matter from petroleum hydrocarbons which are not soluble in acetonitrile. To extract fatty acids from fish liver oils and other animals and vegetable oils. Polar solvent in non-aqueous titrations; non-aqueous solvent for inorganic salts. In, ... UV, and electrochemistry applications. Facilitates reactions between organic substrates and inorganic materials.

The principal organic impurity in commercial acetonitrile is propionitrile; small amounts of allyl alcohol may be present.

Maximum limits of impurities: residue after evaporation 0.0005%, acidity (as acetic acid) 0.03%, alkalinity (as ammonia) 0.001%, water 0.05%. /'Photrex' Reagent, for spectrophotometry/

2023: 25,000,000 - <40,000,000 lb

(1972) PROBABLY GREATER THAN 4.54X10+5 G

(1989) 3.5X10+7 lb

(1991) Exceeded 5000 lb or US $5000 in value

Acetonitrile is listed as a High Production Volume (HPV) chemical (65FR81686). Chemicals listed as HPV were produced in or imported into the U.S. in >1 million pounds in 1990 and/or 1994. The HPV list is based on the 1990 Inventory Update Rule. (IUR) (40 CFR part 710 subpart B; 51FR21438).

For more U.S. Production (Complete) data for ACETONITRILE (7 total), please visit the HSDB record page.

Acetonitrile is mainly prepared by dehydration of acetamide (CH3CONH2) with glacial acetic acid ... or by reacting acetic acid with ammonia at 400-500 °C in the presennce of a dehydration catalyst.

Acetonitrile and hydrogen cyanide are the principal byproducts from the ammoxidation of propylene to acrylonitrile (Sohio process). Some acrylonitrile producers recover and purify acetonitrile, but most companies burn the byproducts as plant fuel.

By-product of propylene-ammonia process for acrylonitrile.

Obtained commercially as a byproduct in manufacture of acrylonitrile. ... Preparation by dehydration of acetamide.

All Other Basic Inorganic Chemical Manufacturing

Acetonitrile: ACTIVE

Most, if not all, of the acetonitrile that was produced commercially in the United States in 1995 was isolated as a by-product from the manufacture of acrylonitrile by propylene ammoxidation.

... can be used as a marker for biomass burning