NITROETHANE
HAZARDTEXT ®
Information to help in the initial response for evaluating chemical incidents
-IDENTIFICATION
SYNONYMS
ETHANE, NITRO- NITROETAN (Polish) NITROETHANE NITROETANO (Portuguese)
IDENTIFIERS
SYNONYM REFERENCE
USES/FORMS/SOURCES
Nitroethane is a nitroparaffin compound used as a solvent for cellulose acetate, cellulose acetopropionate, cellulose acetobutyrate, nitrocellulose, as well as vinyl- and alkyd-compounds, and many other resins, fats, waxes, and dyes. Additionally, it is utilized as a fuel additive, in propellant research, in Friedel-Crafts synthesis, and as a commercial artificial nail remover (Budavari, 1996) Hathaway et al, 1996; (Lewis, 1993; Snyder et al, 1990).
-CLINICAL EFFECTS
GENERAL CLINICAL EFFECTS
- Nitroethane can cause moderate irritation of the eyes, nose, throat, upper respiratory tract and skin. Ingestion can cause nausea, vomiting, and irritation of the mouth and stomach.
- Two children developed methemoglobinemia after ingesting nitroethane-containing artificial nail removing compounds.
- In experimental animals, nitroethane is an eye irritant and can cause narcosis at high concentrations. Other reported effects are respiratory irritation, pulmonary congestion and edema, cerebral edema, fatty degeneration and necrosis of the liver, and edema of the kidneys.
- POTENTIAL HEALTH HAZARDS - EMERGENCY RESPONSE GUIDEBOOK, GUIDE 129 (ERG, 2004)
May cause toxic effects if inhaled or absorbed through skin. Inhalation or contact with material may irritate or burn skin and eyes. Fire will produce irritating, corrosive and/or toxic gases. Vapors may cause dizziness or suffocation. Runoff from fire control or dilution water may cause pollution.
-FIRST AID
FIRST AID AND PREHOSPITAL TREATMENT
EYE EXPOSURE - Immediately wash the eyes with large amounts of water, occasionally lifting the lower and upper lids. Get medical attention immediately. Contact lenses should not be worn when working with this chemical. DERMAL EXPOSURE - Promptly wash the contaminated skin with soap and water. If this chemical penetrates the clothing, promptly remove the clothing and wash the skin with soap and water. Get medical attention promptly. INHALATION EXPOSURE - Move the exposed person to fresh air at once. If breathing has stopped, perform mouth-to-mouth resuscitation. Keep the affected person warm and at rest. Get medical attention as soon as possible. ORAL EXPOSURE - If this chemical has been swallowed, get medical attention immediately. TARGET ORGANS - Skin, respiratory system, CNS, kidneys, and liver (NIOSH , 1997).
Move victims of inhalation exposure from the toxic environment and administer 100% humidified supplemental oxygen with assisted ventilation as required. Exposed skin and eyes should be copiously flushed with water. Because of the potential for rapid onset of CNS depression or seizures with possible aspiration of gastric contents, EMESIS SHOULD NOT BE INDUCED. Cautious gastric lavage followed by administration of activated charcoal may be of benefit if the patient is seen soon after the exposure.
INHALATION: Move patient to fresh air. Monitor for respiratory distress. If cough or difficulty breathing develops, evaluate for respiratory tract irritation, bronchitis, or pneumonitis. Administer oxygen and assist ventilation as required. Treat bronchospasm with an inhaled beta2-adrenergic agonist. Consider systemic corticosteroids in patients with significant bronchospasm. If bronchospasm and wheezing occur, consider treatment with inhaled sympathomimetic agents. ACUTE LUNG INJURY: Maintain ventilation and oxygenation and evaluate with frequent arterial blood gases and/or pulse oximetry monitoring. Early use of PEEP and mechanical ventilation may be needed.
DECONTAMINATION: Remove contaminated clothing and jewelry and place them in plastic bags. Wash exposed areas with soap and water for 10 to 15 minutes with gentle sponging to avoid skin breakdown. A physician may need to examine the area if irritation or pain persists (Burgess et al, 1999). Treat dermal irritation or burns with standard topical therapy. Patients developing dermal hypersensitivity reactions may require treatment with systemic or topical corticosteroids or antihistamines.
DECONTAMINATION: Remove contact lenses and irrigate exposed eyes with copious amounts of room temperature 0.9% saline or water for at least 15 minutes. If irritation, pain, swelling, lacrimation, or photophobia persist after 15 minutes of irrigation, the patient should be seen in a healthcare facility.
Because of the potential for gastrointestinal tract irritation or CNS depression, do NOT induce emesis. Significant esophageal or gastrointestinal tract irritation or burns may occur following ingestion. The possible benefit of early removal of some ingested material by cautious gastric lavage must be weighed against potential complications of bleeding or perforation. GASTRIC LAVAGE: Consider after ingestion of a potentially life-threatening amount of poison if it can be performed soon after ingestion (generally within 1 hour). Protect airway by placement in the head down left lateral decubitus position or by endotracheal intubation. Control any seizures first. ACTIVATED CHARCOAL: Administer charcoal as a slurry (240 mL water/30 g charcoal). Usual dose: 25 to 100 g in adults/adolescents, 25 to 50 g in children (1 to 12 years), and 1 g/kg in infants less than 1 year old. Observe patients with ingestion carefully for the possible development of esophageal or gastrointestinal tract irritation or burns. If signs or symptoms of esophageal irritation or burns are present, consider endoscopy to determine the extent of injury. METHEMOGLOBINEMIA: Determine the methemoglobin concentration and evaluate the patient for clinical effects of methemoglobinemia (ie, dyspnea, headache, fatigue, CNS depression, tachycardia, metabolic acidosis). Treat patients with symptomatic methemoglobinemia with methylene blue (this usually occurs at methemoglobin concentrations above 20% to 30%, but may occur at lower methemoglobin concentrations in patients with anemia, or underlying pulmonary or cardiovascular disorders). Administer oxygen while preparing for methylene blue therapy. METHYLENE BLUE: INITIAL DOSE/ADULT OR CHILD: 1 mg/kg IV over 5 to 30 minutes; a repeat dose of up to 1 mg/kg may be given 1 hour after the first dose if methemoglobin levels remain greater than 30% or if signs and symptoms persist. NOTE: Methylene blue is available as follows: 50 mg/10 mL (5 mg/mL or 0.5% solution) single-dose ampules and 10 mg/1 mL (1% solution) vials. Additional doses may sometimes be required. Improvement is usually noted shortly after administration if diagnosis is correct. Consider other diagnoses or treatment options if no improvement has been observed after several doses. If intravenous access cannot be established, methylene blue may also be given by intraosseous infusion. Methylene blue should not be given by subcutaneous or intrathecal injection. NEONATES: DOSE: 0.3 to 1 mg/kg. Concomitant use of methylene blue with serotonergic drugs, including serotonin reuptake inhibitors (SRIs), selective serotonin reuptake inhibitors (SSRIs), serotonin and norepinephrine reuptake inhibitors (SNRIs), tricyclic antidepressants (TCAs), norepinephrine-dopamine reuptake inhibitors (NDRIs), triptans, and ergot alkaloids may increase the risk of potentially fatal serotonin syndrome.
-MEDICAL TREATMENT
LIFE SUPPORT
- Support respiratory and cardiovascular function.
SUMMARY
- FIRST AID - EMERGENCY RESPONSE GUIDEBOOK, GUIDE 129 (ERG, 2004)
Move victim to fresh air. Call 911 or emergency medical service. Give artificial respiration if victim is not breathing. Administer oxygen if breathing is difficult. Remove and isolate contaminated clothing and shoes. In case of contact with substance, immediately flush skin or eyes with running water for at least 20 minutes. Wash skin with soap and water. Keep victim warm and quiet. In case of burns, immediately cool affected skin for as long as possible with cold water. Do not remove clothing if adhering to skin. Effects of exposure (inhalation, ingestion or skin contact) to substance may be delayed. Ensure that medical personnel are aware of the material(s) involved and take precautions to protect themselves.
FIRST AID EYE EXPOSURE - Immediately wash the eyes with large amounts of water, occasionally lifting the lower and upper lids. Get medical attention immediately. Contact lenses should not be worn when working with this chemical. DERMAL EXPOSURE - Promptly wash the contaminated skin with soap and water. If this chemical penetrates the clothing, promptly remove the clothing and wash the skin with soap and water. Get medical attention promptly. INHALATION EXPOSURE - Move the exposed person to fresh air at once. If breathing has stopped, perform artificial respiration. Keep the affected person warm and at rest. Get medical attention as soon as possible. ORAL EXPOSURE - If this chemical has been swallowed, get medical attention immediately. TARGET ORGANS - Skin, respiratory system, central nervous system, kidneys and liver (National Institute for Occupational Safety and Health, 2007).
SUPPORT Move victims of inhalation exposure from the toxic environment and administer 100% humidified supplemental oxygen with assisted ventilation as required. Exposed skin and eyes should be copiously flushed with water. Because of the potential for rapid onset of CNS depression or seizures with possible aspiration of gastric contents, EMESIS SHOULD NOT BE INDUCED. Cautious gastric lavage followed by administration of activated charcoal may be of benefit if the patient is seen soon after the exposure.
INHALATION EXPOSURE INHALATION: Move patient to fresh air. Monitor for respiratory distress. If cough or difficulty breathing develops, evaluate for respiratory tract irritation, bronchitis, or pneumonitis. Administer oxygen and assist ventilation as required. Treat bronchospasm with an inhaled beta2-adrenergic agonist. Consider systemic corticosteroids in patients with significant bronchospasm. If bronchospasm and wheezing occur, consider treatment with inhaled sympathomimetic agents. ACUTE LUNG INJURY: Maintain ventilation and oxygenation and evaluate with frequent arterial blood gases and/or pulse oximetry monitoring. Early use of PEEP and mechanical ventilation may be needed.
DERMAL EXPOSURE DECONTAMINATION: Remove contaminated clothing and jewelry and place them in plastic bags. Wash exposed areas with soap and water for 10 to 15 minutes with gentle sponging to avoid skin breakdown. A physician may need to examine the area if irritation or pain persists (Burgess et al, 1999). Treat dermal irritation or burns with standard topical therapy. Patients developing dermal hypersensitivity reactions may require treatment with systemic or topical corticosteroids or antihistamines.
EYE EXPOSURE DECONTAMINATION: Remove contact lenses and irrigate exposed eyes with copious amounts of room temperature 0.9% saline or water for at least 15 minutes. If irritation, pain, swelling, lacrimation, or photophobia persist after 15 minutes of irrigation, the patient should be seen in a healthcare facility.
ORAL EXPOSURE Because of the potential for gastrointestinal tract irritation or CNS depression, do NOT induce emesis. Significant esophageal or gastrointestinal tract irritation or burns may occur following ingestion. The possible benefit of early removal of some ingested material by cautious gastric lavage must be weighed against potential complications of bleeding or perforation. GASTRIC LAVAGE: Consider after ingestion of a potentially life-threatening amount of poison if it can be performed soon after ingestion (generally within 1 hour). Protect airway by placement in the head down left lateral decubitus position or by endotracheal intubation. Control any seizures first. ACTIVATED CHARCOAL: Administer charcoal as a slurry (240 mL water/30 g charcoal). Usual dose: 25 to 100 g in adults/adolescents, 25 to 50 g in children (1 to 12 years), and 1 g/kg in infants less than 1 year old. Observe patients with ingestion carefully for the possible development of esophageal or gastrointestinal tract irritation or burns. If signs or symptoms of esophageal irritation or burns are present, consider endoscopy to determine the extent of injury. METHEMOGLOBINEMIA: Determine the methemoglobin concentration and evaluate the patient for clinical effects of methemoglobinemia (ie, dyspnea, headache, fatigue, CNS depression, tachycardia, metabolic acidosis). Treat patients with symptomatic methemoglobinemia with methylene blue (this usually occurs at methemoglobin concentrations above 20% to 30%, but may occur at lower methemoglobin concentrations in patients with anemia, or underlying pulmonary or cardiovascular disorders). Administer oxygen while preparing for methylene blue therapy. METHYLENE BLUE: INITIAL DOSE/ADULT OR CHILD: 1 mg/kg IV over 5 to 30 minutes; a repeat dose of up to 1 mg/kg may be given 1 hour after the first dose if methemoglobin levels remain greater than 30% or if signs and symptoms persist. NOTE: Methylene blue is available as follows: 50 mg/10 mL (5 mg/mL or 0.5% solution) single-dose ampules and 10 mg/1 mL (1% solution) vials. Additional doses may sometimes be required. Improvement is usually noted shortly after administration if diagnosis is correct. Consider other diagnoses or treatment options if no improvement has been observed after several doses. If intravenous access cannot be established, methylene blue may also be given by intraosseous infusion. Methylene blue should not be given by subcutaneous or intrathecal injection. NEONATES: DOSE: 0.3 to 1 mg/kg. Concomitant use of methylene blue with serotonergic drugs, including serotonin reuptake inhibitors (SRIs), selective serotonin reuptake inhibitors (SSRIs), serotonin and norepinephrine reuptake inhibitors (SNRIs), tricyclic antidepressants (TCAs), norepinephrine-dopamine reuptake inhibitors (NDRIs), triptans, and ergot alkaloids may increase the risk of potentially fatal serotonin syndrome.
Significant, symptomatic methemoglobinemia may require treatment with intravenous methylene blue. Inhaled sympathomimetic bronchodilators could be required if bronchiolar spasm develops following oxides of nitrogen exposure, while corticosteroid administration is controversial in this setting.
-RANGE OF TOXICITY
MINIMUM LETHAL EXPOSURE
MAXIMUM TOLERATED EXPOSURE
Rats exposed to 2200 ppm for 6 hours demonstrated no noticeable problems (ACGIH, 1991). Rabbits exposed to 2500 ppm for 3 hours survived, but at a level of 5000 ppm for 3 hours fatalities were universal (Hathaway et al, 1996). In one study, guinea pigs, monkeys, and rabbits were exposed to nitroethane levels of 500-30,000 ppm for durations of from 30 minutes to 140 total hours. In these three species, a level of 500 ppm was generally safe and well-tolerated. A level of 1000 ppm was often lethal (ACGIH, 1991).
- Carcinogenicity Ratings for CAS79-24-3 :
ACGIH (American Conference of Governmental Industrial Hygienists, 2010): Not Listed ; Listed as: Nitroethane EPA (U.S. Environmental Protection Agency, 2011): Not Listed IARC (International Agency for Research on Cancer (IARC), 2016; International Agency for Research on Cancer, 2015; IARC Working Group on the Evaluation of Carcinogenic Risks to Humans, 2010; IARC Working Group on the Evaluation of Carcinogenic Risks to Humans, 2010a; IARC Working Group on the Evaluation of Carcinogenic Risks to Humans, 2008; IARC Working Group on the Evaluation of Carcinogenic Risks to Humans, 2007; IARC Working Group on the Evaluation of Carcinogenic Risks to Humans, 2006; IARC, 2004): Not Listed NIOSH (National Institute for Occupational Safety and Health, 2007): Not Listed ; Listed as: Nitroethane MAK (DFG, 2002): Not Listed NTP (U.S. Department of Health and Human Services, Public Health Service, National Toxicology Project ): Not Listed
TOXICITY AND RISK ASSESSMENT VALUES
- EPA Risk Assessment Values for CAS79-24-3 (U.S. Environmental Protection Agency, 2011):
ACGIH, 1991 Budavari, 1996 Lewis, 1996 RTECS, 1997 Snyder et al., 1990) LCLo- (INHALATION)GUINEA_PIG: LCLo- (INHALATION)MOUSE: LCLo- (INHALATION)RABBIT: LCLo- (INHALATION)RAT: LD50- (INTRAPERITONEAL)MOUSE: LD50- (ORAL)MOUSE: LD50- (ORAL)RABBIT: LD50- (ORAL)RAT: LDLo- (ORAL)RABBIT: LDLo- (INTRAPERITONEAL)RAT: TDLo- (ORAL)HUMAN:
CALCULATIONS
-STANDARDS AND LABELS
WORKPLACE STANDARDS
- ACGIH TLV Values for CAS79-24-3 (American Conference of Governmental Industrial Hygienists, 2010):
Editor's Note: The listed values are recommendations or guidelines developed by ACGIH(R) to assist in the control of health hazards. They should only be used, interpreted and applied by individuals trained in industrial hygiene. Before applying these values, it is imperative to read the introduction to each section in the current TLVs(R) and BEI(R) Book and become familiar with the constraints and limitations to their use. Always consult the Documentation of the TLVs(R) and BEIs(R) before applying these recommendations and guidelines.
- AIHA WEEL Values for CAS79-24-3 (AIHA, 2006):
- NIOSH REL and IDLH Values for CAS79-24-3 (National Institute for Occupational Safety and Health, 2007):
Listed as: Nitroethane REL: TWA: 100 ppm (310 mg/m(3)) STEL: Ceiling: Carcinogen Listing: (Not Listed) Not Listed Skin Designation: Not Listed Note(s):
IDLH: IDLH: 1000 ppm Note(s): Not Listed
- OSHA PEL Values for CAS79-24-3 (U.S. Occupational Safety, and Health Administration (OSHA), 2010):
- OSHA List of Highly Hazardous Chemicals, Toxics, and Reactives for CAS79-24-3 (U.S. Occupational Safety and Health Administration, 2010):
ENVIRONMENTAL STANDARDS
- EPA CERCLA, Hazardous Substances and Reportable Quantities for CAS79-24-3 (U.S. Environmental Protection Agency, 2010):
- EPA CERCLA, Hazardous Substances and Reportable Quantities, Radionuclides for CAS79-24-3 (U.S. Environmental Protection Agency, 2010):
- EPA RCRA Hazardous Waste Number for CAS79-24-3 (U.S. Environmental Protection Agency, 2010b):
- EPA SARA Title III, Extremely Hazardous Substance List for CAS79-24-3 (U.S. Environmental Protection Agency, 2010):
- EPA SARA Title III, Community Right-to-Know for CAS79-24-3 (40 CFR 372.65, 2006; 40 CFR 372.28, 2006):
- DOT List of Marine Pollutants for CAS79-24-3 (49 CFR 172.101 - App. B, 2005):
- EPA TSCA Inventory for CAS79-24-3 (EPA, 2005):
SHIPPING REGULATIONS
- DOT -- Table of Hazardous Materials and Special Provisions for UN/NA Number 2842 (49 CFR 172.101, 2005):
- ICAO International Shipping Name for UN2842 (ICAO, 2002):
LABELS
- NFPA Hazard Ratings for CAS79-24-3 (NFPA, 2002):
Listed as: Nitroethane Hazard Ratings: Health Rating (Blue): 2 Flammability Rating (Red): 3 (3) Flammable. Liquids and solids that can be ignited under almost all ambient temperature conditions. Including liquids with a flash point below 73 degrees F and a boiling point above 100 degrees F, solid materials which form coarse dusts that burn rapidly without becoming explosive, materials which burn rapidly by reason of self-contained oxygen (ie, organic peroxides), and materials which ignite spontaneously when exposed to air.
Instability Rating (Yellow): 3 (3) Materials which in themselves are capable of detonation but which require a strong initiating source, or which must be heated first. This rating includes materials which are shock sensitive at elevated temperatures, and which react explosively with water without requiring heat.
Oxidizer/Water-Reactive Designation: Not Listed
-HANDLING AND STORAGE
HANDLING
- Nitroethane is stable during transport (CHRIS , 1997).
- According to 49 CFR 171.2: "No person may /transport,/ offer or accept a hazardous material for transportation in commerce unless that material is properly classed, described, packaged, marked, labeled, and in condition for shipment as required or authorized by.../the hazardous materials regulations (49 CFR 171 to 177)" (HSDB , 1997)
STORAGE
Nitroethane is usually shipped in glass bottles, drums, tank cars and trucks (NFPA, 1994). Protect containers from physical damage (ITI, 1995).
- ROOM/CABINET RECOMMENDATIONS
The storage temperature is to be ambient (CHRIS , 1997). Open venting, with a flame arrester, should be utilized (CHRIS , 1997). Outside or detached storage is optimal (ITI, 1995; NFPA, 1994). Inside storage should be within a standard, flammable liquids storage room or explosion-proof refrigerator (Sittig, 1991).
Keep this compound well separated from oxidizing materials and other flammables (ITI, 1995; NFPA, 1994). Nitroethane is incompatible with: calcium hydroxide as well as other hydroxides (potassium hydroxide, sodium hydroxide), hydrocarbons, metal oxides, strong inorganic bases, strong acids, and amine (HSDB , 1997; Lewis, 1996; NFPA, 1994; Urben, 1995).
-PERSONAL PROTECTION
SUMMARY
- RECOMMENDED PROTECTIVE CLOTHING - EMERGENCY RESPONSE GUIDEBOOK, GUIDE 129 (ERG, 2004)
- Appropriate personal protective clothing should be worn to prevent contact with nitroethane. If skin contact occurs, washing with large amounts of soap and water should be done immediately. Due to the flammability hazard, contaminated or wet clothing should be removed and replaced immediately. No specific recommendation is made for persons working with this compound to change into uncontaminated clothing before leaving the job site (AAR, 1996; (NIOSH , 1997).
EYE/FACE PROTECTION
- Appropriate eye protection should be worn to prevent contact with this compound (NIOSH , 1997; Sittig, 1991).
RESPIRATORY PROTECTION
- Refer to "Recommendations for respirator selection" in the NIOSH Pocket Guide to Chemical Hazards on TOMES Plus(R) for respirator information.
PROTECTIVE CLOTHING
- CHEMICAL PROTECTIVE CLOTHING. Search results for CAS 79-24-3.
-PHYSICAL HAZARDS
FIRE HAZARD
POTENTIAL FIRE OR EXPLOSION HAZARDS - EMERGENCY RESPONSE GUIDEBOOK, GUIDE 129 (ERG, 2004) HIGHLY FLAMMABLE: Will be easily ignited by heat, sparks or flames. Vapors may form explosive mixtures with air. Vapors may travel to source of ignition and flash back. Most vapors are heavier than air. They will spread along ground and collect in low or confined areas (sewers, basements, tanks). Vapor explosion hazard indoors, outdoors or in sewers. Those substances designated with a "P" may polymerize explosively when heated or involved in a fire. Runoff to sewer may create fire or explosion hazard. Containers may explode when heated. Many liquids are lighter than water.
Nitroethane is a flammable liquid. It is considered a moderate hazard when exposed to open flame, heat, sparks, or oxidizers (Lewis, 1993; Lewis, 1996; NFPA, 1994). The vapors are heavier than air, so flashback along a vapor trail is possible (AAR, 1996; (NFPA, 1994). This compound may float or sink in water (AAR, 1996; (CHRIS , 1997).
- FLAMMABILITY CLASSIFICATION
- NFPA Flammability Rating for CAS79-24-3 (NFPA, 2002):
Listed as: Nitroethane Flammability Rating: 3 (3) Flammable. Liquids and solids that can be ignited under almost all ambient temperature conditions. Including liquids with a flash point below 73 degrees F and a boiling point above 100 degrees F, solid materials which form coarse dusts that burn rapidly without becoming explosive, materials which burn rapidly by reason of self-contained oxygen (ie, organic peroxides), and materials which ignite spontaneously when exposed to air.
- FIRE CONTROL/EXTINGUISHING AGENTS
- FIRE PRECAUTIONS - EMERGENCY RESPONSE GUIDEBOOK, GUIDE 129 (ERG, 2004)
- SMALL FIRE PRECAUTIONS - EMERGENCY RESPONSE GUIDEBOOK, GUIDE 129 (ERG, 2004)
Dry chemical, CO2, water spray or alcohol-resistant foam. Do not use dry chemical extinguishers to control fires involving nitromethane or nitroethane.
- LARGE FIRE PRECAUTIONS - EMERGENCY RESPONSE GUIDEBOOK, GUIDE 129 (ERG, 2004)
Water spray, fog or alcohol-resistant foam. Do not use straight streams. Move containers from fire area if you can do it without risk.
- TANK OR CAR/TRAILER LOAD FIRE PRECAUTIONS - EMERGENCY RESPONSE GUIDEBOOK, GUIDE 129 (ERG, 2004)
Fight fire from maximum distance or use unmanned hose holders or monitor nozzles. Cool containers with flooding quantities of water until well after fire is out. Withdraw immediately in case of rising sound from venting safety devices or discoloration of tank. ALWAYS stay away from tanks engulfed in fire. For massive fire, use unmanned hose holders or monitor nozzles; if this is impossible, withdraw from area and let fire burn.
- NFPA Extinguishing Methods for CAS79-24-3 (NFPA, 2002):
- To fight a fire involving nitroethane, use dry chemical, carbon dioxide, or foam; "alcohol" foam is not effective. Water may be ineffective on the fire itself, and solid streams of may spread the fire. However, water spray can be utilized in flooding quantities to cool fire-exposed containers/structures. Combat the fire from as great a distance as possible or from a protected area (AAR, 1996; (CHRIS , 1997; Lewis, 1996; NFPA, 1994).
EXPLOSION HAZARD
- Nitroethane decomposes explosively when heated. Closed containers may violently rupture at high temperatures (Lewis, 1996; NFPA, 1994).
- The vapor can explode if ignited within an enclosed area (CHRIS , 1997).
- Do not heat this compound with easily oxidized hydrocarbons under confinement (NFPA, 1994).
- As a class of compounds, nitroparaffins form a salt in the presence of water and an inorganic base. The dry salts are explosive (NFPA, 1994).
DUST/VAPOR HAZARD
- Toxic nitrogen oxide fumes, carbon dioxide, and carbon monoxide are released when this compound is heated to decomposition (Lewis, 1996; NFPA, 1994).
REACTIVITY HAZARD
- Nitroethane is incompatible with: calcium hydroxide as well as other hydroxides (potassium hydroxide, sodium hydroxide), hydrocarbons, metal oxides, strong inorganic bases, strong acids, and amines (HSDB , 1997; Lewis, 1996; NFPA, 1994; Urben, 1995).
- It has a high heat of absorption. Rapid absorption of the gas or anhydrous liquid on activated carbon (or Hopcalite) may result in flames (Budavari, 1996).
- This compound may attack some plastics (CHRIS , 1997).
EVACUATION PROCEDURES
- Editor's Note: This material is not listed in the Table of Initial Isolation and Protective Action Distances.
- LARGE SPILL - PUBLIC SAFETY EVACUATION DISTANCES - EMERGENCY RESPONSE GUIDEBOOK, GUIDE 129 (ERG, 2004)
- FIRE - PUBLIC SAFETY EVACUATION DISTANCES - EMERGENCY RESPONSE GUIDEBOOK, GUIDE 129 (ERG, 2004)
If tank, rail car or tank truck is involved in a fire, ISOLATE for 800 meters (1/2 mile) in all directions; also, consider initial evacuation for 800 meters (1/2 mile) in all directions.
- PUBLIC SAFETY MEASURES - EMERGENCY RESPONSE GUIDEBOOK, GUIDE 129 (ERG, 2004)
CALL Emergency Response Telephone Number on Shipping Paper first. If Shipping Paper not available or no answer, refer to appropriate telephone number: MEXICO: SETIQ: 01-800-00-214-00 in the Mexican Republic; For calls originating in Mexico City and the Metropolitan Area: 5559-1588; For calls originating elsewhere, call: 011-52-555-559-1588.
CENACOM: 01-800-00-413-00 in the Mexican Republic; For calls originating in Mexico City and the Metropolitan Area: 5550-1496, 5550-1552, 5550-1485, or 5550-4885; For calls originating elsewhere, call: 011-52-555-550-1496, or 011-52-555-550-1552; 011-52-555-550-1485, or 011-52-555-550-4885.
ARGENTINA: CIQUIME: 0-800-222-2933 in the Republic of Argentina; For calls originating elsewhere, call: +54-11-4613-1100.
BRAZIL: PRÓ-QUÍMICA: 0-800-118270 (Toll-free in Brazil); For calls originating elsewhere, call: +55-11-232-1144 (Collect calls are accepted).
COLUMBIA: CISPROQUIM: 01-800-091-6012 in Colombia; For calls originating in Bogotá, Colombia, call: 288-6012; For calls originating elsewhere, call: 011-57-1-288-6012.
CANADA: UNITED STATES:
For additional details see the section entitled "WHO TO CALL FOR ASSISTANCE" under the ERG Instructions. As an immediate precautionary measure, isolate spill or leak area for at least 50 meters (150 feet) in all directions. Keep unauthorized personnel away. Stay upwind. Keep out of low areas. Ventilate closed spaces before entering.
- AIHA ERPG Values for CAS79-24-3 (AIHA, 2006):
- DOE TEEL Values for CAS79-24-3 (U.S. Department of Energy, Office of Emergency Management, 2010):
Listed as Nitroethane TEEL-0 (units = ppm): 100 TEEL-1 (units = ppm): 100 TEEL-2 (units = ppm): 200 TEEL-3 (units = ppm): 1,000 Definitions: TEEL-0: The threshold concentration below which most people will experience no adverse health effects. TEEL-1: The airborne concentration (expressed as ppm [parts per million] or mg/m(3) [milligrams per cubic meter]) of a substance above which it is predicted that the general population, including susceptible individuals, could experience notable discomfort, irritation, or certain asymptomatic, nonsensory effects. However, these effects are not disabling and are transient and reversible upon cessation of exposure. TEEL-2: The airborne concentration (expressed as ppm or mg/m(3)) of a substance above which it is predicted that the general population, including susceptible individuals, could experience irreversible or other serious, long-lasting, adverse health effects or an impaired ability to escape. TEEL-3: The airborne concentration (expressed as ppm or mg/m(3)) of a substance above which it is predicted that the general population, including susceptible individuals, could experience life-threatening adverse health effects or death.
- AEGL Values for CAS79-24-3 (National Research Council, 2010; National Research Council, 2009; National Research Council, 2008; National Research Council, 2007; NRC, 2001; NRC, 2002; NRC, 2003; NRC, 2004; NRC, 2004; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2006; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2007; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2005; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2005; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2007; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2006; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2006; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2006; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2006; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2006; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2006; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2006; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2006; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2006; United States Environmental Protection Agency Office of Pollution Prevention and Toxics, 2006; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2006; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2007; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2007; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2008; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2008; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2007; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2008; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2007; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2008; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2007; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2009; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2009; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2009; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2009; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2009; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2009; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2009; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2009; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2009; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2009; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2009; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2008; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2008; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2008; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2008; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2008; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2008; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2008; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2009; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2008; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2008; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2008; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2009; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2008; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2008; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2008; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2008; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2008; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2008; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2008; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2007; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2006; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2006; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2006; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2007; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2007; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2007; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2007; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2007; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2005; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2005; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2005; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2005; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2005; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2005; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2005; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2005; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2007; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2005; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2006; 62 FR 58840, 1997; 65 FR 14186, 2000; 65 FR 39264, 2000; 65 FR 77866, 2000; 66 FR 21940, 2001; 67 FR 7164, 2002; 68 FR 42710, 2003; 69 FR 54144, 2004):
- NIOSH IDLH Values for CAS79-24-3 (National Institute for Occupational Safety and Health, 2007):
IDLH: 1000 ppm Note(s): Not Listed
CONTAINMENT/WASTE TREATMENT OPTIONS
SPILL OR LEAK PRECAUTIONS - EMERGENCY RESPONSE GUIDEBOOK, GUIDE 129 (ERG, 2004) ELIMINATE all ignition sources (no smoking, flares, sparks or flames in immediate area). All equipment used when handling the product must be grounded. Do not touch or walk through spilled material. Stop leak if you can do it without risk. Prevent entry into waterways, sewers, basements or confined areas. A vapor suppressing foam may be used to reduce vapors. Absorb or cover with dry earth, sand or other non-combustible material and transfer to containers. Use clean non-sparking tools to collect absorbed material.
RECOMMENDED PROTECTIVE CLOTHING - EMERGENCY RESPONSE GUIDEBOOK, GUIDE 129 (ERG, 2004) Stay upwind of the spill to avoid any contact with this material. Remove all possible ignition sources from the area. Stop the leak if possible. Water spray can be employed to protect personnel as well as disperse and cool vapors. Runoff should be isolated for proper disposal; dikes may be used to control the flow (CHRIS , 1997; NFPA, 1994).
Absorbent materials (e.g., paper towels) can be used to pick up spilled nitroethane. After being used, store these materials within sealed, vapor-tight plastic bags for later disposal (HSDB , 1997; Sittig, 1991).
For small amounts of nitroethane, the materials (paper towels) used to absorb the spill can be burned in a combustion chamber equipped with an appropriate effluent gas cleaning device (HSDB , 1997). Larger amounts of nitroethane can be disposed of by mixing with fuel oil, and then atomizing within a suitable combustion chamber (HSDB , 1997). Waste management activities associated with material disposition are unique to individual situations. Proper waste characterization and decisions regarding waste management should be coordinated with the appropriate local, state, or federal authorities to ensure compliance with all applicable rules and regulations.
-ENVIRONMENTAL HAZARD MANAGEMENT
POLLUTION HAZARD
POLLUTION SOURCES Nitroethane may be released to the environment through various waste streams associated with its production and use as a solvent, chemical intermediate, and experimental liquid propellant (HSDB, 2004).
OCCUPATIONAL EXPOSURE Workers may be exposed to nitroethane during its production or subsequent use. Main routes of exposure are dermal and inhalation (HSDB, 2004). Occupational exposure is likely the most probable reason for human exposure (HSDB, 2004).
ENVIRONMENTAL FATE AND KINETICS
Nitroethane is expected to exist solely as a vapor in the ambient atmosphere, based on its estimated vapor pressure of 20.8 mmHg (at 25 degrees C) (HSDB, 2004). It is degraded in the air through reaction with photochemically-produced hydroxyl radicals, with a rate constant of 1.5 x 10(-13) cm(3)/molecule-sec (at 25 degrees C). The half-life for this reaction is approximately 107 days (assuming a hydroxyl radical concentration of 5 x 10(5) radicals/cm(3)) (HSDB, 2004).
SURFACE WATER Nitroethane is not expected to adsorb to sediment or suspended solids in water, based on an estimated organic carbon-water partition coefficient (Koc) of 30. However, experimental results showing adsorption of nitromethane to high-organic carbon peat indicate that nitromethane may adsorb to organic sediments present in the water (HSDB, 2004). A measured Henry's Law constant of 4.76 x 10(-5) atm-cm(3)/mole indicates that nitromethane may volatilize from water surfaces. Half-lives for this reaction have been estimated at 19 hours for a model river (1 m deep, flowing at 1 m/sec, wind velocity of 3 m/sec), and 8 days for a model lake (1 m deep, flowing at 0.05 m/sec, wind velocity of 0.5 m/sec) (HSDB, 2004).
TERRESTRIAL Nitromethane is expected to have very high mobility in soil, based on its organic carbon-water partition coefficient (Koc) of 30. However, experimental results showing adsorption of nitromethane to high-organic carbon peat indicate that nitromethane may adsorb to organic material present in the soil and reduce its mobility (HSDB, 2004). Vapor sorption for nitromethane of almost 80 mg vapor uptake/g dry high-organic carbon peat (at a relative pressure of 0.3 at 24 degrees C) was measured at over a 2 - 3 week period. From this, a partition capacity of 272 mg/g peat (at relative pressure of 1) was calculated (HSDB, 2004). Nitromethane's nitro group may promote hydrogen bonding to clay in soils, which could significantly affect its mobility in soils (HSDB, 2004). The polarity of the nitromethane molecule may allow for hydrophilic-coordinative adsorption (HSDB, 2004).
A Henry's Law constant of 4.76 x 10(-5) atm-cm(3)/mole indicates that volatilization from moist soil surfaces may be a significant fate process for nitromethane. Volatilization from dry soil surfaces may also occur, based on an estimated vapor pressure of 20.8 mmHg (at 25 degrees C) (HSDB, 2004). Nitromethane may aerobically biodegrade, however limited data exist on its biodegradability (HSDB, 2004).
ABIOTIC DEGRADATION
- Nitromethane exists primarily as vapor or a liquid in the atmosphere and soil, respectively (HSDB, 2004).
- It is expected to be relatively mobile in soils, but may adsorb to high organic carbon-content matter. Significant volatilization from moist soil surfaces is also expected, and may also occur from dry soils (HSDB, 2004).
- In water, nitroethane may adsorb to suspended solids and sediment. Volatilization from water surfaces is expected (HSDB, 2004).
- Nitromethane is degraded in the environment through reaction with photochemically-produced hydroxyl radicals in the atmosphere. It may also undergo aerobic biodegradation in soils and water (HSDB, 2004).
BIODEGRADATION
- Limited experimental data indicate that nitroethane may biodegrade under aerobic conditions, but not under anaerobic conditions (HSDB, 2004).
BIOACCUMULATION
ENVIRONMENTAL TOXICITY
- The effect of low concentrations of nitromethane on aquatic organisms is unknown, however, it may be dangerous if it enters water intakes (CHRIS, 2004).
-PHYSICAL/CHEMICAL PROPERTIES
MOLECULAR WEIGHT
DESCRIPTION/PHYSICAL STATE
- Nitroethane is a colorless, oily liquid which possesses a pleasant yet slightly irritating "fruity" odor (Budavari, 1996; Lewis, 1996; NIOSH , 1997).
VAPOR PRESSURE
- 15.6 mmHg (at 20 degrees C) (Lewis, 1993; NFPA, 1994)
- 20.8 mmHg (at 25 degrees C) (calculated) (HSDB , 1997)
- 20.9 mmHg (at 25 degrees C) (ACGIH, 1991)
- 21 mmHg (at 77 degrees F) (NIOSH , 1997)
SPECIFIC GRAVITY
- NORMAL TEMPERATURE AND PRESSURE
(25 degrees C; 77 degrees F and 760 mmHg) 1.046 (25/25 degrees C) (Lewis, 1996) 1.041 (25/25 degrees C) (Budavari, 1996) 1.0448 (25/4 degrees C) (HSDB , 1997)
- OTHER TEMPERATURE AND/OR PRESSURE
DENSITY
- OTHER TEMPERATURE AND/OR PRESSURE
FREEZING/MELTING POINT
-89.5 degrees C (Chemsoft(R) , 1996) -90 degrees C; -130 degrees F (Lewis, 1996; NFPA, 1994) -50 degrees C (Budavari, 1996; Lewis, 1996)
BOILING POINT
- 114-115 degrees C (Budavari, 1996)
- 114 degrees C; 237 degrees F; 387 degrees K (CHRIS , 1997; Lewis, 1996; NFPA, 1994; NIOSH , 1997)
FLASH POINT
- 41 degrees C; 106 degrees F (Lewis, 1993; Sittig, 1991)
- 41.11 degrees C; 106 degrees F (open cup) (Budavari, 1996)
- 41 degrees C (open cup) (ACGIH, 1991)
- 105 degrees F (open cup) (CHRIS , 1997)
- 28 degrees C; 82 degrees F (NFPA, 1994; NIOSH , 1997)
- 27.78 degrees C (ITI, 1995)
- 87 degrees F (closed cup) (CHRIS , 1997)
- 31 degrees C (closed cup) (ACGIH, 1991)
AUTOIGNITION TEMPERATURE
- 414 degrees C; 778 degrees F (Lewis, 1996; NFPA, 1994)
- 415 degrees C; 779 degrees F (Lewis, 1993)
- 414.9 degrees C (ITI, 1995)
EXPLOSIVE LIMITS
4.0% (Budavari, 1996; Lewis, 1996) 3.4% (Chemsoft(R) , 1996; NFPA, 1994; NIOSH , 1997)
SOLUBILITY
Nitroethane is slightly soluble in hot water, and insoluble in cold water (Lewis, 1996; NFPA, 1994). 4.5 mL nitroethane/100 mL water (at 20 degrees C) (Budavari, 1996; Lewis, 1993) 4.5x10(4) mg/L (at 25 degrees C) (HSDB , 1997) 5% soluble by weight (NIOSH , 1997)
This compound is miscible with methanol, ethanol, ether, chloroform, and acetone (ACGIH, 1991; Budavari, 1996; Lewis, 1996). It is soluble in chloroform and aqueous solutions of alkalies (Budavari, 1996).
OCTANOL/WATER PARTITION COEFFICIENT
- log Kow = 0.18 (HSDB , 1997)
HENRY'S CONSTANT
- 4.76x10(-5) atm-m(3)/mol (at 25 degrees C) (HSDB , 1997)
SPECTRAL CONSTANTS
88 (Atlas of Mass Spectral Data, John Wiley & Sons, New York) (HSDB , 1997) 24 (National Bureau of Standards EPA-NIH Mass Spectra Data Base, NSRDS-NBS-63) (HSDB , 1997)
OTHER/PHYSICAL
1.3917 (at 20 degrees C) (Budavari, 1996; Lewis, 1993) 1.39007 (at 24.3 degrees C) (Budavari, 1996)
- NUCLEAR MAGNETIC RESONANCE
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