FORMIC ACID
HAZARDTEXT ®
Information to help in the initial response for evaluating chemical incidents
-IDENTIFICATION
SYNONYMS
IDENTIFIERS
SYNONYM REFERENCE
- (HSDB , 1995; RTECS , 1995)
USES/FORMS/SOURCES
Formic acid is a natural constituent of some fruits, nuts, and dairy products (Clayton & Clayton, 1994). Some wines may contain formic acid. Concentrations in the following produce: apples, pears, plums, and apricots ranged from 2.7 to 87 mg/L.
-CLINICAL EFFECTS
GENERAL CLINICAL EFFECTS
- Formic acid can be irritating or corrosive to the skin, eyes, and mucous membranes, depending on the concentration. It may cause severe caustic injury to the skin, eyes, or mucosal membranes.
- Symptoms of acute ingestion (50 grams or more) can initially include salivation, bloody vomiting, a burning sensation in the mouth and pharynx, diarrhea, severe pain. Circulatory collapse and death have occurred following exposure.
- In limited case reports, intentional oral ingestions of formic acid have resulted in life-threatening metabolic acidosis, profound hypotension, shock, ARDS, acute renal failure, and severe hemolysis. Systemic effects have also been reported following dermal exposure.
- Occupational exposure has caused nausea and albumin or blood in the urine. Formic acid is a sensitizer for some individuals; allergic contact dermatitis or possibly asthma could develop in these individuals.
- Combining formic and sulfuric acid produces carbon monoxide; severe carbon monoxide poisoning has resulted.
- POTENTIAL HEALTH HAZARDS - EMERGENCY RESPONSE GUIDEBOOK, GUIDE 153 (ERG, 2004)
TOXIC; inhalation, ingestion or skin contact with material may cause severe injury or death. Contact with molten substance may cause severe burns to skin and eyes. Avoid any skin contact. Effects of contact or inhalation may be delayed. Fire may produce irritating, corrosive and/or toxic gases. Runoff from fire control or dilution water may be corrosive and/or toxic and cause pollution.
ACUTE CLINICAL EFFECTS
- Formic acid is a STRONG ACID, and consequently is a CORROSIVE or irritant, depending on its concentration. Concentrated solutions can cause severe damage and ulceration of the skin, eyes, and mucous membranes (Clayton & Clayton, 1982).
- The vapor was more potent as an irritant than was formaldehyde in guinea pigs (Clayton & Clayton, 1982). It is readily absorbed following inhalation (Clayton & Clayton, 1982), and direct contact with the eye can produce corneal opacity.
- If ingested, formic acid can cause salivation, vomiting, a burning sensation in the GI tract, severe pain, and circulatory collapse.
CHRONIC CLINICAL EFFECTS
- Occupational exposure to an airborne concentration of approximately 15 ppm of formic acid caused nausea, but apparently no other ill effects (ACGIH, 1986) except perhaps albumin or blood in the urine.
- Formic acid is a SENSITIZER and some exposed persons may develop allergic contact dermatitis or occupational asthma.
-FIRST AID
FIRST AID AND PREHOSPITAL TREATMENT
If no respiratory compromise is present, administer milk or water as soon as possible after ingestion. The exact ideal amount is unknown; no more than 8 ounces (240 mL) in adults and 4 ounces (120 mL) in children is recommended to minimize the risk of vomiting (Caravati, 2004). USE OF DILUENTS IS CONTROVERSIAL: While experimental models have suggested that immediate dilution may lessen caustic injury (Homan et al, 1993; Homan et al, 1994; Homan et al, 1995), this has not been adequately studied in humans. DILUENT TYPE: Use any readily available nontoxic, cool liquid. Both milk and water have been shown to be effective in experimental studies of caustic ingestion (Maull et al, 1985a; Rumack & Burrington, 1977; Homan et al, 1995; Homan et al, 1994; Homan et al, 1993). ADVERSE EFFECTS: Potential adverse effects include vomiting and airway compromise (Caravati, 2004). CONTRAINDICATIONS: Do NOT attempt dilution in patients with respiratory distress, altered mental status, severe abdominal pain, nausea or vomiting, or patients who are unable to swallow or protect their airway. Diluents should not be force fed to any patient who refuses to swallow (Rao & Hoffman, 2002).
-MEDICAL TREATMENT
LIFE SUPPORT
- Support respiratory and cardiovascular function.
SUMMARY
- FIRST AID - EMERGENCY RESPONSE GUIDEBOOK, GUIDE 153 (ERG, 2004)
Move victim to fresh air. Call 911 or emergency medical service. Give artificial respiration if victim is not breathing. Do not use mouth-to-mouth method if victim ingested or inhaled the substance; give artificial respiration with the aid of a pocket mask equipped with a one-way valve or other proper respiratory medical device. 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. For minor skin contact, avoid spreading material on unaffected skin. Keep victim warm and quiet. 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 - Immediately flush the contaminated skin with water. If this chemical penetrates the clothing, immediately remove the clothing and flush the skin with 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 - Eyes, skin, and respiratory system (National Institute for Occupational Safety and Health, 2007).
GENERAL - 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. Ingestion may result in significant esophageal or gastrointestinal tract irritation or burns, and 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.
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.
INGESTION EXPOSURE - Do NOT induce emesis. DILUTION: If no respiratory compromise is present, administer milk or water as soon as possible after ingestion. Dilution may only be helpful if performed in the first seconds to minutes after ingestion. The ideal amount is unknown; no more than 8 ounces (240 mL) in adults and 4 ounces (120 mL) in children is recommended to minimize the risk of vomiting. 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. 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.
-RANGE OF TOXICITY
MINIMUM LETHAL EXPOSURE
The lowest published lethal dose of formic acid for a woman via ingestion is 2,440 mcg/kg (RTECS , 2000). Accidental or intentional overdoses (50 grams or more) are reported to produce salivation, vomiting (which may be bloody), a burning sensation in the mouth and pharynx, diarrhea, and severe pain. Circulatory collapse may follow, causing death (Clayton & Clayton, 1994). CASE REPORT - A 56-year-old male died of cardiac arrest and multiple organ system failure 10 days after ingesting an unknown amount of a descaling agent which contained 55% formic acid, 1.6% phosphoric acid, and 4% quinoline (Jacques, 1982). CASE REPORT - A 27-year-old male died approximately 26 hours after intentional ingestion of a decalcifying agent. The patient developed immediate vomiting and was transported to a hospital. Signs and symptoms of massive acidosis, excessive hemolysis, bleeding complications and eventually hepatic and renal failure occurred. It was estimated that the patient had ingested at least 30 to 60 grams (44 to 88 mL) of a solution containing 60% formic acid (Westphal et al, 2001). CASE SERIES - Jefferys & Wiseman (1980) found that in a review of 45 patients who had ingested formic acid, painful deaths occurred in 14 of 16 patients who ingested between 45 to 200 grams of formic acid. The majority died from corrosive perforation of the abdominal viscera within the first 36 hours of exposure (Jefferys & Wiseman, 1980). CASE SERIES - Three fatalities were reported following ingestion of household descaling agents which contained between 40% to 55% formic acid. One patient died of refractory hypotension, and postmortem exam revealed extensive erosion of the esophagus, stomach, and duodenum following a 50 to 100 mL ingestion of a kitchen descaling agent containing 55% formic acid (Naik et al, 1980).
MAXIMUM TOLERATED EXPOSURE
CASE REPORT - A 36-year-old female ingested 110 grams of formic acid and developed acute renal failure, requiring intensive supportive care. Recovery was complete with the exception of intermittent dilation needed for persistent esophageal stricture (Moore et al, 1994). CASE SERIES - In retrospective review of 45 cases of formic acid poisoning, 34 were found to be deliberate ingestions. Of those cases, 23 ingested between 5 and 30 grams of formic acid, and no deaths occurred. Serious toxicity was reported following ingestions between 30 to 45 grams (Jefferys & Wiseman, 1980).
The lowest published toxic concentration of formic acid for a man via inhalation is 7,300 mcg/m(3)/8 hours (RTECS , 1995). Workers exposed to a mixture of formic and acetic acids at an average concentration of 15 ppm each complained of nausea (Hathaway et al, 1991).
In studies of rats repeatedly exposed to oral doses (up to 360 mg/kg) of formic acid in drinking water, no adverse effects were reported with the exception of weight loss and decreased appetite. Likewise, Swiss mice exposed to formic acid (8% solution in water) painted on the ears did not develop any adverse effects (Clayton & Clayton, 1994).
- Carcinogenicity Ratings for CAS64-18-6 :
ACGIH (American Conference of Governmental Industrial Hygienists, 2010): Not Listed ; Listed as: Formic acid EPA (U.S. Environmental Protection Agency, 2011): Not Assessed under the IRIS program. ; Listed as: Formic acid 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: Formic acid 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 CAS64-18-6 (U.S. Environmental Protection Agency, 2011):
Oral: Inhalation: Drinking Water:
-STANDARDS AND LABELS
WORKPLACE STANDARDS
- ACGIH TLV Values for CAS64-18-6 (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 CAS64-18-6 (AIHA, 2006):
- NIOSH REL and IDLH Values for CAS64-18-6 (National Institute for Occupational Safety and Health, 2007):
Listed as: Formic acid REL: IDLH: IDLH: 30 ppm Note(s): Not Listed
- OSHA PEL Values for CAS64-18-6 (U.S. Occupational Safety, and Health Administration (OSHA), 2010):
- OSHA List of Highly Hazardous Chemicals, Toxics, and Reactives for CAS64-18-6 (U.S. Occupational Safety and Health Administration, 2010):
ENVIRONMENTAL STANDARDS
- EPA CERCLA, Hazardous Substances and Reportable Quantities for CAS64-18-6 (U.S. Environmental Protection Agency, 2010):
- EPA CERCLA, Hazardous Substances and Reportable Quantities, Radionuclides for CAS64-18-6 (U.S. Environmental Protection Agency, 2010):
- EPA RCRA Hazardous Waste Number for CAS64-18-6 (U.S. Environmental Protection Agency, 2010b):
Listed as: Formic acid P or U series number: U123 Footnote: Editor's Note: The D, F, and K series waste numbers and Appendix VIII to Part 261 -- Hazardous Constituents were not included. Please refer to 40 CFR Part 261.
- EPA SARA Title III, Extremely Hazardous Substance List for CAS64-18-6 (U.S. Environmental Protection Agency, 2010):
- EPA SARA Title III, Community Right-to-Know for CAS64-18-6 (40 CFR 372.65, 2006; 40 CFR 372.28, 2006):
- DOT List of Marine Pollutants for CAS64-18-6 (49 CFR 172.101 - App. B, 2005):
- EPA TSCA Inventory for CAS64-18-6 (EPA, 2005):
SHIPPING REGULATIONS
- DOT -- Table of Hazardous Materials and Special Provisions for UN/NA Number 1779 (49 CFR 172.101, 2005):
- ICAO International Shipping Name for UN1779 (ICAO, 2002):
LABELS
- NFPA Hazard Ratings for CAS64-18-6 (NFPA, 2002):
Listed as: Formic Acid Hazard Ratings: Health Rating (Blue): 3 (3) Seriously toxic material. Short term exposure could cause serious temporary or residual injury even though prompt medical treatment is given. Includes known or suspect small animal carcinogens, mutagens, or teratogens.
Flammability Rating (Red): 2 Instability Rating (Yellow): 0 Oxidizer/Water-Reactive Designation: Not Listed
-HANDLING AND STORAGE
STORAGE
- ROOM/CABINET RECOMMENDATIONS
-PERSONAL PROTECTION
SUMMARY
- RECOMMENDED PROTECTIVE CLOTHING - EMERGENCY RESPONSE GUIDEBOOK, GUIDE 153 (ERG, 2004)
Wear positive pressure self-contained breathing apparatus (SCBA). Wear chemical protective clothing that is specifically recommended by the manufacturer. It may provide little or no thermal protection. Structural firefighters' protective clothing provides limited protection. fire situations ONLY; it is not effective in spill situations where direct contact with the substance is possible.
- Avoid breathing vapors. Keep upwind. Avoid bodily contact with the material. Wear appropriate chemical protective gloves, boots, and goggles. Do not handle broken packages unless wearing appropriate personal protective equipment. Wash away any material which may have contacted the body with copious amounts of water or soap and water. If contact with the material is anticipated, wear appropriate chemical protective clothing (AAR, 1992).
- Clothing contaminated with formic acid should be placed in closed containers for storage until it can be discarded or until provision is made for the removal of formic acid from the clothing. If the clothing is to be laundered or otherwise cleaned to remove the formic acid, the person performing the operation should be informed of formic acid's hazardous properties (HSDB , 1995).
- Wash immediately when skin becomes contaminated. Immediately remove non-impervious clothing that becomes contaminated (HSDB , 1995).
EYE/FACE PROTECTION
- Emergency showers and eyewash should be provided (HSDB , 1995).
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 64-18-6.
-PHYSICAL HAZARDS
FIRE HAZARD
POTENTIAL FIRE OR EXPLOSION HAZARDS - EMERGENCY RESPONSE GUIDEBOOK, GUIDE 153 (ERG, 2004) Combustible material: may burn but does not ignite readily. When heated, vapors may form explosive mixtures with air: indoors, outdoors and sewers explosion hazards. Those substances designated with a "P" may polymerize explosively when heated or involved in a fire. Contact with metals may evolve flammable hydrogen gas. Containers may explode when heated. Runoff may pollute waterways. Substance may be transported in a molten form.
Formic acid is a flammable liquid when exposed to heat or flame. It can react vigorously with oxidizing materials (Lewis, 1992).
- FLAMMABILITY CLASSIFICATION
- NFPA Flammability Rating for CAS64-18-6 (NFPA, 2002):
Listed as: Formic Acid Flammability Rating: 2
- INITIATING OR CONTRIBUTING PROPERTIES
- FIRE CONTROL/EXTINGUISHING AGENTS
- SMALL FIRE PRECAUTIONS - EMERGENCY RESPONSE GUIDEBOOK, GUIDE 153 (ERG, 2004)
- LARGE FIRE PRECAUTIONS - EMERGENCY RESPONSE GUIDEBOOK, GUIDE 153 (ERG, 2004)
Dry chemical, CO2, alcohol-resistant foam or water spray. Move containers from fire area if you can do it without risk. Dike fire control water for later disposal; do not scatter the material.
- TANK OR CAR/TRAILER LOAD FIRE PRECAUTIONS - EMERGENCY RESPONSE GUIDEBOOK, GUIDE 153 (ERG, 2004)
Fight fire from maximum distance or use unmanned hose holders or monitor nozzles. Do not get water inside containers. 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.
- NFPA Extinguishing Methods for CAS64-18-6 (NFPA, 2002):
- Use water spray, dry chemical, "alcohol resistant" foam, or carbon dioxide. Use water spray to keep fire-exposed containers cool (NFPA, 1991).
- Use water in flooding quantities as fog. Solid streams of water may be ineffective. Apply water from as far a distance as possible. Use water spray to knock down vapors (AAR, 1992).
EXPLOSION HAZARD
- During preparation of peroxyformic acid by a patented procedure involving interaction of carboxylic acids with hydrogen peroxide in the presence of metaboric acid, an explosion may occur which can be attributed to spontaneous separation of concentrated peroxyformic acid (Bretherick, 1990).
- Formic acid forms an explosive reaction with the following (Lewis, 1992; NFPA, 1991):
DUST/VAPOR HAZARD
- Vapors are irritating and painful to breath. Vapor exposure may cause nausea and vomiting (CHRIS , 1995).
REACTIVITY HAZARD
- Formic acid may react with alkalies and oxidizing materials such as peroxides, nitric acid, and chromic acid. Formic acid decomposes slowly during storage and more rapidly under fire conditions, forming carbon monoxide (NFPA, 1991).
- Aluminum reduces formic acid (itself a reductant) with incandescence (Bretherick, 1990).
- Formic acid is incompatible with concentrated sulfuric acid (NIOSH, 1995).
- Formic acid is a flammable liquid when exposed to heat or flame. It can react vigorously with oxidizing materials (Lewis, 1992).
- Formic acid is a strong reducing agent (Budavari, 1989).
- During preparation of peroxyformic acid by a patented procedure involving interaction of carboxylic acids with hydrogen peroxide in the presence of metaboric acid, an explosion may occur which can be attributed to spontaneous separation of concentrated peroxyformic acid (Bretherick, 1990).
- Formic acid forms an explosive reaction with the following (Lewis, 1992; NFPA, 1991):
EVACUATION PROCEDURES
- Editor's Note: This material is not listed in the Table of Initial Isolation and Protective Action Distances.
- SPILL - PUBLIC SAFETY EVACUATION DISTANCES - EMERGENCY RESPONSE GUIDEBOOK, GUIDE 153 (ERG, 2004)
Increase, in the downwind direction, as necessary, the isolation distance of at least 50 meters (150 feet) for liquids and at least 25 meters (75 feet) for solids in all directions.
- FIRE - PUBLIC SAFETY EVACUATION DISTANCES - EMERGENCY RESPONSE GUIDEBOOK, GUIDE 153 (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 153 (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 in all directions for at least 50 meters (150 feet) for liquids and at least 25 meters (75 feet) for solids. Keep unauthorized personnel away. Stay upwind. Keep out of low areas. Ventilate enclosed areas.
- AIHA ERPG Values for CAS64-18-6 (AIHA, 2006):
- DOE TEEL Values for CAS64-18-6 (U.S. Department of Energy, Office of Emergency Management, 2010):
- AEGL Values for CAS64-18-6 (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; 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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 CAS64-18-6 (National Institute for Occupational Safety and Health, 2007):
IDLH: 30 ppm Note(s): Not Listed
CONTAINMENT/WASTE TREATMENT OPTIONS
SPILL OR LEAK PRECAUTIONS - EMERGENCY RESPONSE GUIDEBOOK, GUIDE 153 (ERG, 2004) ELIMINATE all ignition sources (no smoking, flares, sparks or flames in immediate area). Do not touch damaged containers or spilled material unless wearing appropriate protective clothing. Stop leak if you can do it without risk. Prevent entry into waterways, sewers, basements or confined areas. Absorb or cover with dry earth, sand or other non-combustible material and transfer to containers. DO NOT GET WATER INSIDE CONTAINERS.
RECOMMENDED PROTECTIVE CLOTHING - EMERGENCY RESPONSE GUIDEBOOK, GUIDE 153 (ERG, 2004) Wear positive pressure self-contained breathing apparatus (SCBA). Wear chemical protective clothing that is specifically recommended by the manufacturer. It may provide little or no thermal protection. Structural firefighters' protective clothing provides limited protection. fire situations ONLY; it is not effective in spill situations where direct contact with the substance is possible.
At the time of this review, criteria for land treatment or burial (sanitary landfill) disposal practices are subject to significant revision. Prior to implementing land disposal of waste residue (including waste sludge), consult with environmental regulatory agencies for guidance on acceptable disposal practices (HSDB , 1995).
Eliminate all ignition sources. 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. Neutralize spill and washings with soda ash or lime. Report any release in excess of 5000 pounds (NFPA, 1991). Keep sparks, flames, and other sources of ignition away. Keep material out of water sources and sewers. Build dikes to contain flow as necessary (AAR, 1992). Land Spill: Dig a pit, pond, lagoon, or holding area to contain liquid or solid material (AAR, 1992). Land Spill: Dike surface flow using soil, sand bags, foamed polyurethane, or foamed concrete (AAR, 1992). Land Spill: Absorb bulk liquid with fly ash or cement powder (AAR, 1992). Land Spill: Neutralize with agricultural lime, crushed limestone, or sodium bicarbonate (AAR, 1992). Water Spill: Neutralize with agricultural lime, crushed limestone, or sodium bicarbonate (AAR, 1992). Water Spill: Use mechanical dredges or lifts to remove immobilized masses of pollutants and precipitates (AAR, 1992). Air Release: Apply water spray or mist to knock down vapors (AAR, 1992). Air Release: Vapor knockdown water is corrosive or toxic and should be diked for containment (AAR, 1992).
Formic acid is a good candidate for liquid injection incineration at a temperature range of 650 to 1600 degrees C and a residence time of 0.1 to 2 seconds (HSDB , 1995). It is also a good candidate for rotary kiln incineration at a temperature range of 820 to 1600 degrees C and residence times of seconds for liquids and gases, and hours for solids (HSDB , 1995). Formic acid is also a good candidate for fluidized bed incineration at a temperature range of 450 to 980 degrees C and residence times of seconds for liquids and gases, and longer for solids (HSDB , 1995). 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
- Formic acid occurs naturally in plants and insects. It is also a product of microbial metabolism of organic matter and is produced in the photooxidation of biogenic and anthropogenic compounds. Formic acid will also be released to the environment as emissions and in wastewater in its production and various industrial uses (HSDB, 2004).
ENVIRONMENTAL FATE AND KINETICS
In the atmosphere, formic acid will be rapidly scavenged by rain and dissolve in cloud water and aerosols. It participates in reactions in clouds and aerosols involving dissolved hydroxyl radicals. The vapor phase acid also reacts with photochemically produced hydroxyl radicals (half-life 36 days) and possibly with alkenes that may be present in polluted urban air (HSDB, 2004). In the atmosphere, formic acid reacts with photochemically produced hydroxyl radicals with a half-life of 36 days (HSDB, 2004).
SURFACE WATER Based on the results of screening studies, formic acid should biodegrade if released in water. It should not adsorb significantly to sediment. Bioconcentration in aquatic organisms is not expected to be an important fate process (HSDB, 2004). The Henry's Law Constant for formic acid is 1.67 x 10(-7) atm-m(3)/mole, indicating that volatilization from water would not be significant (HSDB, 2004).
TERRESTRIAL If released on land, formic acid should leach into some soils where it would probably biodegrade based upon the results of screening studies (HSDB, 2004). Formic acid is miscible in water. Chemicals that are soluble in water do not usually adsorb significantly to soil or sediment due to hydrophobic forces. However, at ambient pHs, formic acid exists as the ion and may therefore have the potential to bind to clay or humic material by coulombic forces. However, no evidence of such binding has been reported (HSDB, 2004).
ABIOTIC DEGRADATION
- Formic acid can be degraded chemically to innocuous substances in most environments. Screening studies indicate biodegradation is likely in water and soil. It will generally leach to subsurface soil and then biodegrade. Adsorption to aquatic sediment is not expected to be significant, nor is volatilization from water based on the Henry's Law Constant [1.67 x 10(-7) atm-m(3)/mole]. Airborne concentrations are dissolved in cloud water or aerosols present in the atmosphere where reactions can occur with dissolved hydroxyl radicals. The vapor (acid form) reacts with photochemically produced hydroxyl radicals and possibly with alkenes present in air pollution (HSDB, 2004).
BIODEGRADATION
- Formic acid biodegrades readily in screening tests. It can be degraded biologically to innocuous substances in most environments (HSDB, 2004).
BIOACCUMULATION
Formic acid has a log octanol/water partition coefficient of minus 0.54 from which a bioconcentration factor (BCF) of 0.22 can be estimated using a recommended regression equation. Therefore, formic acid should not bioconcentrate in aquatic organisms (HSDB, 2004).
ENVIRONMENTAL TOXICITY
- ECOTOXICITY VALUES (HSDB, 2004):
TLm, Lepomis macrochirus (bluegill), 175 mg/L/24 hr, fresh water, conditions of bioassay not specified TLm, Daphnia, 120 ppm/L/48 hr, fresh water, conditions of bioassay not specified
-PHYSICAL/CHEMICAL PROPERTIES
MOLECULAR WEIGHT
DESCRIPTION/PHYSICAL STATE
- Formic acid is a colorless, fuming liquid with a pungent, penetrating odor, and sour taste (Lewis, 1996; Budavari, 1996; HSDB , 2000).
PH
- In an aqeous solution (pKa= 3.76, compared with 4.76 for acetic acid) (HSDB , 2000).
VAPOR PRESSURE
- 40 mmHg (at 24.0 degrees C) (Lewis, 1992)
- 23-33 mmHg (at 20 degrees C) (ACGIH, 1991)
- 35 mmHg (at 20 degrees C) (Clayton & Clayton, 1982)
SPECIFIC GRAVITY
- OTHER TEMPERATURE AND/OR PRESSURE
LIQUID: 1.220 (at 20/4 degrees C) (Budavari, 1989) LIQUID: 1.2267 (at 15/4 degrees C) (Lewis, 1992)
FREEZING/MELTING POINT
BOILING POINT
- 100.5 degrees C (Budavari, 1989)
FLASH POINT
- 68.89 degrees C; 156 degrees F (open cup) (Lewis, 1992; NFPA, 1991)
- 50 degrees C; 122 degrees F (for a 90% aqueous solution) (NFPA, 1991)
AUTOIGNITION TEMPERATURE
- 1114 degrees F (Lewis, 1992; NFPA, 1991)
- 813 degrees F (for a 90% aqueous solution) (Lewis, 1992; NFPA, 1991)
EXPLOSIVE LIMITS
SOLUBILITY
OCTANOL/WATER PARTITION COEFFICIENT
- log Kow = -0.54 (HSDB , 1995)
HENRY'S CONSTANT
- 1.67x10(-7) atm-m(3)/mol (HSDB , 1995)
SPECTRAL CONSTANTS
OTHER/PHYSICAL
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