POTASSIUM, METAL
HAZARDTEXT ®
Information to help in the initial response for evaluating chemical incidents
-IDENTIFICATION
SYNONYMS
Kalium Potassium Potassium, metal Elemental potassium
IDENTIFIERS
2257-Potassium 2257-Potassium, metal
SYNONYM REFERENCE
- (Bingham et al, 2001; Budavari, 2001; HSDB, 2003; Pohanish, 2002)
USES/FORMS/SOURCES
Uses of potassium metal encompass a broad range, including laboratory reagents, fertilizers, liquid detergents, fireworks, heat-transfer alloys in nuclear reactor systems and high-reading thermometers, and preparation of potassium peroxide. It is primarily used in the making of NaK-78, a sodium-potassium alloy. Potassium is also used as a reducing agent, such as in the seeding of combustion gases in magnetohydrodynamic generators or for oxygen generation in oxygen breathing apparatus (Ashford, 2001; Bingham et al, 2001; HSDB, 2003; ILO, 1998a; Lewis, 2001; Pohanish, 2002). Potassium metal is used in the synthesis of inorganic potassium compounds; in organic syntheses involving condensation, dehalogenation, reduction, and polymerization reactions; and as a heat transfer medium with sodium. The radioactive isotope is used in geological dating methods (Budavari, 2001). It is a component of fertilizers used in agriculture (ILO, 1998a).
Potassium is a Group 1A alkali metal. It has a body-centered cubic structure (Budavari, 2001). Potassium metal is a shiny, silver, soft metallic substance. Oxidation will cause it to tarnish when exposed to air, and it will normally appear silver- or greyish-white. It is considered by NFPA to be a combustible solid (AAR, 2002; Ashford, 2001; Lewis, 2000; NFPA, 2002; Bingham et al, 2001). Naturally occurring isotopes of potassium include: 39 (93.26%); 40 (0.012%), which is radioactive; and 41 (6.73%) (Budavari, 2001). Recognized grades reported in industrial literature include technical and 99.95% pure (Lewis, 2001). Available forms include up to 99.99% pure; high-purity grade (packed under argon), technical grade (packed under nitrogen), and bricks (packed under oil)(HSDB, 2003) . Impurities in the material may include oxygen, carbon, hydrogen, alkali metals, aluminum, calcium, copper, boron, or silicon. Iron, nickel, and chromium may also be impurities resulting from leaching of these metals from container materials. High purity potassium, for example, may have impurities of <30 ppm oxygen, <100 ppm transition metals, and <50 ppm other alkali metals (HSDB, 2003).
Potassium is a naturally occurring alkali metal. It is the seventh most abundant element and exists in combination in nature, such as in ores of carnallite, sylvite, and polyhalite. It is found primarily as the chloride (sylvite), and also in the aluminosilicates, orthoclase and microcline. It makes up 1.5 - 2.59% by weight of the earth's crust (Bingham et al, 2001; Budavari, 2001; Lewis, 1998; Lewis, 2001). It was first prepared in free form in 1807 by Davy through electrolysis of fused potassium hydroxide (Budavari, 2001). The primary method of production in the United States is thermochemical distillation of potassium chloride with sodium. Reduction/fractionation processes using these substances are also used to produce potassium (Ashford, 2001; Lewis, 2001). Industrial production is by chemical reduction (Budavari, 2001).
-CLINICAL EFFECTS
GENERAL CLINICAL EFFECTS
- Potassium metal (K) or elemental potassium is a corrosive, highly flammable and explosive substance. The metal reacts violently on exposure to water or moist air. Exposure routes include skin, eyes or lungs. Fumes from explosion or burning are also highly toxic. Ingestion is unlikely.
- Short term exposure to fumes or dusts may cause skin and mucus membrane irritation. Irritation of the eyes, nose, throat and lungs, with sneezing, coughing and sore throat may occur.
- Higher exposures or direct metal contact may cause severe burns from the exothermic reaction of the metal with water. Burns may also occur from the formation of potassium hydroxide produced in the chemical reaction. First, second and third degree burns have been reported. Severe eye irritation, burns or permanent eye damage may occur. Acute lung injury and death from toxic fumes or particles is possible.
- Chronic exposure to fumes may result in nasal and inner septum sores and bronchitis.
- POTENTIAL HEALTH HAZARDS - EMERGENCY RESPONSE GUIDEBOOK, GUIDE 138 (ERG, 2004)
Inhalation or contact with vapors, substance or decomposition products may cause severe injury or death. May produce corrosive solutions on contact with water. Fire will produce irritating, corrosive and/or toxic gases. Runoff from fire control may cause pollution.
-MEDICAL TREATMENT
LIFE SUPPORT
- Support respiratory and cardiovascular function.
SUMMARY
- FIRST AID - EMERGENCY RESPONSE GUIDEBOOK, GUIDE 138 (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, wipe from skin immediately; flush skin or eyes with running water for at least 20 minutes. Keep victim warm and quiet. Ensure that medical personnel are aware of the material(s) involved and take precautions to protect themselves.
GENERAL - In the presence of water, metallic potassium (K) is an explosion hazard. It is also corrosive and highly flammable. Metallic potassium burn management differs from standard alkaline chemical burn treatment in that WATER IS CONTRAINDICATED in the initial management. Potassium may ignite on contact with water and leave a highly caustic residue (Herbert & Lawrence, 1989).
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. Seek medical attention immediately. The use of humidified oxygen is not recommended. 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 - Contaminated clothing should be removed immediately. Blot or wipe any residue from the skin. Remove any metal particles from the skin or wound with a dry forceps. Cover the burn with mineral or cooking oil, if available. Washing or lavage of the skin with water is contraindicated initially(Clare & Krenzelok, 1988). Place fragments of metal removed from skin and clothing in a container of pure tertbutyl alcohol for safe disposal. Dry xylene is also an acceptable medium for potassium metal storage (Krenzelok, 1992). Wounds and burn areas may require debridement and/or surgical extraction of deeply imbedded particles. Once all metal has been removed, the area may be irrigated with water. See Corrosives-Alkaline management for further treatment.
EYE EXPOSURE - ORAL EXPOSURE - Ingestion of elemental potassium is unlikely. Should ingestion occur, keep the patient NPO and seek medical treatment immediately. Gastric decontamination, lavage or prehospital activated charcoal is NOT recommended. 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
MAXIMUM TOLERATED EXPOSURE
- Carcinogenicity Ratings for CAS7440-09-7 :
ACGIH (American Conference of Governmental Industrial Hygienists, 2010): Not Listed 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 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 CAS7440-09-7 (U.S. Environmental Protection Agency, 2011):
-STANDARDS AND LABELS
WORKPLACE STANDARDS
- ACGIH TLV Values for CAS7440-09-7 (American Conference of Governmental Industrial Hygienists, 2010):
- AIHA WEEL Values for CAS7440-09-7 (AIHA, 2006):
- NIOSH REL and IDLH Values for CAS7440-09-7 (National Institute for Occupational Safety and Health, 2007):
- OSHA PEL Values for CAS7440-09-7 (U.S. Occupational Safety, and Health Administration (OSHA), 2010):
- OSHA List of Highly Hazardous Chemicals, Toxics, and Reactives for CAS7440-09-7 (U.S. Occupational Safety and Health Administration, 2010):
ENVIRONMENTAL STANDARDS
- EPA CERCLA, Hazardous Substances and Reportable Quantities for CAS7440-09-7 (U.S. Environmental Protection Agency, 2010):
- EPA CERCLA, Hazardous Substances and Reportable Quantities, Radionuclides for CAS7440-09-7 (U.S. Environmental Protection Agency, 2010):
- EPA RCRA Hazardous Waste Number for CAS7440-09-7 (U.S. Environmental Protection Agency, 2010b):
- EPA SARA Title III, Extremely Hazardous Substance List for CAS7440-09-7 (U.S. Environmental Protection Agency, 2010):
- EPA SARA Title III, Community Right-to-Know for CAS7440-09-7 (40 CFR 372.65, 2006; 40 CFR 372.28, 2006):
- DOT List of Marine Pollutants for CAS7440-09-7 (49 CFR 172.101 - App. B, 2005):
- EPA TSCA Inventory for CAS7440-09-7 (EPA, 2005):
SHIPPING REGULATIONS
- DOT -- Table of Hazardous Materials and Special Provisions for UN/NA Number 2257 (49 CFR 172.101, 2005):
- ICAO International Shipping Name for UN2257 (ICAO, 2002):
LABELS
- NFPA Hazard Ratings for CAS7440-09-7 (NFPA, 2002):
-HANDLING AND STORAGE
SUMMARY
Full PPE, including respiratory protection, is necessary when handling potassium metal due to its high reactivity and associated caustic and corrosive characteristics. Emergency response to spills or fire situations may require implementation of SCBA with chemical protective gear. It is combustible and presents a dangerous fire and explosion hazard (AAR, 2002; CHRIS, 2003; NFPA, 2002; Lewis, 2000; Pohanish, 2002). Potassium must be handled, stored, and packaged for transport under specific conditions that avoid its oxidation or any contact with incompatible materials. It undergoes a violent reaction with a number of chemical substances, and can explode or ignite upon contact with water or air. It should be separated from other chemicals that present a potential reactivity hazard (AAR, 2002; CHRIS, 2003; NFPA, 2002; Lewis, 2000; Pohanish, 2002). Potassium should be kept away from sources of ignition, and explosion-proof electrical equipment and fittings should be used where it is handled, used, manufactured, or stored (Pohanish, 2002).
- PUBLIC HEALTH CONSIDERATIONS
Patients received at an emergency department with potassium metal exposure will require wound debridement and metal fragment removal. Water is contraindicated in the initial management of exposure due to the hazards associated with the reactivity of potassium metal with water. Extracted potassium fragments can be placed in pure tertbutyl alcohol for eventual disposal (Clare & Krenzelok, 1988).
HANDLING
- Training on the proper handling and storage of potassium metal is suggested for individuals working with or around this chemical. It presents serious fire, explosion, reactivity, and toxicity hazards of which workers should be aware of for safe handling and storage (Pohanish, 2002).
- When handling potassium metal, the use of protective gloves and clothing will prevent the likelihood of skin contact. Respiratory and eye/face protection are also recommended. Broken packages in transport should not be handled unless proper PPE is worn (AAR, 2002; Pohanish, 2002).
- Potassium should not be handled or stored near sources of ignition due to the potential for fire or explosion hazard (Pohanish, 2002)
- Explosion-proof electrical equipment and fittings should be used where potassium is handled, used, manufactured, or stored (Pohanish, 2002).
- Handling procedures should consider the dangerous fire and explosion hazards associated with potassium metal, its peroxide and superoxide. Oxidized potassium metal stored under oil may explode violently when handled or cut (Bingham et al, 2001; Lewis, 2000; NFPA, 1997; Pohanish & Greene, 1997).
- Potassium metal is considered stable for transport if protected from air and water. It may be stored under mineral oil, kerosene, nitrogen, argon, or liquid that contains no oxygen, such as liquid petrolatum or petroleum. It is inert to the saturated aliphatic and aromatic hydrocarbons (Budavari, 2001; CHRIS, 2003; HSDB, 2003; Lewis, 2000; Pohanish, 2002).
- Cutting and handling of oxidized potassium for disposal purposes is recommended to be completed under dry xylene under a hood (Urben, 1999).
STORAGE
The usual shipping container for potassium metal is a hermetically sealed can shipped inside a wooden box. Other common shipping containers are metal cans, pails, drums, or tanks, including tanks on trucks rail cars or barges. It should be packaged under inert gas or mineral oil (NFPA, 2002). Containers should be kept away from water and protected from physical damage. Potassium must be maintained in storage under liquid containing no oxygen. It can also be stored under nitrogen or kerosene (ITI, 1995; Lewis, 1998; Pohanish, 2002). Storage under dry xylene in airtight containers is recommended to prevent oxidation of fresh potassium (Urben, 1999). Store metallic potassium in inert atmospheres, such as argon or nitrogen, under liquids that are oxygen-free, such as toluene or kerosene, or in glass capsules filled under vacuum or inert atmosphere (Lewis, 2001). Containers should be labelled for shipping as "dangerous when wet"; DOT Class 4.3, dangerous when wet material (NFPA, 2002). Never store potassium under halogenated hydrocarbons (ITI, 1995). Storage containers should prevent contact with carbon monoxide and moisture, compounds of heavy metals, and carbon tetrachloride to control the potential for violent reactions (Pohanish, 2002).
- ROOM/CABINET RECOMMENDATIONS
Potassium metal is incompatible with a broad range of substances. Its highly reactive characteristics should be thoroughly considered when establishing storage conditions for the material (Bingham et al, 2001; Lewis, 2000; NFPA, 2002; Pohanish & Greene, 1997; Pohanish, 2002). Potassium metal should be kept under liquid that does not contain oxygen (Budavari, 2001). Separate stored potassium metal from water, acids, halogens, silicates, sulfates, nitrates, carbonates, phosphates, oxides and hydroxides of heavy metals, organics, and Teflon (NFPA, 2002) . Oxidized metal should not come into contact with organic materials to avoid an explosion hazard. Oxidation can occur at room temperature, including when the material is stored under oil. The metal forms potassium peroxide (K2O2) and superoxide (KO3 or K2O4) which can explode on contact with organic material. The explosion is caused by interaction of residual traces of mineral oil or other organic contaminant, not the potassium metal, and is initiated by the pressure of dry cutting or impact (Lewis, 2000; Urben, 1999). Potassium stored in aluminum containers is reported to have led to severe corrosion and perforation of the container. The corrosion occurred as a result of potassium carbonate formation from atmospheric carbon dioxide inside the container (Urben, 1999).
-PERSONAL PROTECTION
SUMMARY
- RECOMMENDED PROTECTIVE CLOTHING - EMERGENCY RESPONSE GUIDEBOOK, GUIDE 138 (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 in fire situations ONLY; it is not effective in spill situations where direct contact with the substance is possible.
- Personal protective equipment (PPE) is necessary for emergency response or when handling potassium as it is corrosive and highly toxic through skin contact, ingestion, and inhalation. It is a severe irritant to the skin, eyes, and membranes, strongly caustic to tissues, and causes severe eye and skin burns. An additional toxic inhalation hazard exists from fumes released in a fire situation (Bingham et al, 2001; ITI, 1995; NFPA, 2002).
- Emergency response PPE should include special chemical protective clothing, gloves, boots, goggles, and positive pressure self-contained breathing apparatus (SCBA) (AAR, 2002; CHRIS, 2003; NFPA, 2002).
EYE/FACE PROTECTION
- Contact lenses should not be worn when potassium metal is being handled in the workplace or in an emergency response situation (Pohanish, 2002).
- Dust-proof chemical goggles and face shield are recommended unless a full-face respirator is used (CHRIS, 2003; Pohanish, 2002).
RESPIRATORY PROTECTION
- Where the potential for inhalation exposure exists, a MSHA/NIOSH approved respirator should be used with particulate filters capable of collecting dusts, fumes, and mists. A MSHA/NIOSH approved supplied-air respirator or a positive pressure self-contained breathing apparatus (SCBA) are recommended where high potassium inhalation exposure may occur or in emergency response situations (AAR, 2002; NFPA, 2002; Pohanish, 2002).
PROTECTIVE CLOTHING
- CHEMICAL PROTECTIVE CLOTHING. Search results for CAS 7440-09-7.
ENGINEERING CONTROLS
- Cutting and handling of oxidized potassium for disposal purposes is recommended to be completed under dry xylene and under a hood (Urben, 1999).
OTHER
- INDUSTRIAL DECONTAMINATION
In instances of exposure to potassium metal, immediately seek medical attention. Do not use water for personnel decontamination (Clare & Krenzelok, 1988; Pohanish, 2002). Wipe material from skin immediately and quickly remove contaminated clothing and shoes. Isolate the contaminated items. Metal particles should be removed from the eyes, skin, or wound immediately. Burn areas should be covered with oil, such as mineral or cooking oil, to insulate any unreacted metal (AAR, 2002; Clare & Krenzelok, 1988). In instances of inhalation exposure, the individual should be removed from the exposure area to an area with fresh air (Pohanish, 2002) Provide emergency showers and eyewash stations (Pohanish, 2002).
-PHYSICAL HAZARDS
FIRE HAZARD
POTENTIAL FIRE OR EXPLOSION HAZARDS - EMERGENCY RESPONSE GUIDEBOOK, GUIDE 138 (ERG, 2004) Produce flammable gases on contact with water. May ignite on contact with water or moist air. Some react vigorously or explosively on contact with water. May be ignited by heat, sparks or flames. May re-ignite after fire is extinguished. Some are transported in highly flammable liquids. Runoff may create fire or explosion hazard.
Potassium metal presents a dangerous fire hazard. It is a combustible solid which, once ignited, burns violently. Contact with a number of substances can lead to fire and/or explosion due to its high reactivity. For example, contact with air causes spontaneous ignition; contact with water releases flammable hydrogen gas, and the heat of the reaction ignites the material. Potassium metal can also ignite with just the presence of moisture (AAR, 2002; Bingham et al, 2001; CHRIS, 2003; Lewis, 2000; NFPA, 1997; Pohanish, 2002; Pohanish & Greene, 1997; NFPA, 1997). Storage in aluminum cans has been reported to lead to fire from corrosion of the container. There is also risk of fire if powdered potassium, or potassium sand, dispersed in benzene is exposed to air. Fires occurred when potassium was blotted with filter paper to take up solvent used to remove traces of oil (Urben, 1999). Potassium metal burns with a characteristic violet colored flame (Budavari, 2001).
- FLAMMABILITY CLASSIFICATION
- NFPA Flammability Rating for CAS7440-09-7 (NFPA, 2002):
- INITIATING OR CONTRIBUTING PROPERTIES
Contact with water can readily lead to fire due to the generation of flammable hydrogen gas and ignition of the metal from the heat of reaction (Bingham et al, 2001). Due to its reactivity with water, potassium could potentially ignite damp combustible materials. On the converse, if the potassium material is damp, it will readily burn in combination with combustible materials (CHRIS, 2003; NFPA, 2002). Storage of potassium in an aluminum container was reported to cause a fire. Oxidation of the stored potassium material to potassium oxides corroded an aluminum can. The oil in which the potassium was stored was released, exposing the material to accelerated oxidation (Urben, 1999). Molten potassium ignites in acetylene (HSDB, 2003).
- FIRE CONTROL/EXTINGUISHING AGENTS
- FIRE PRECAUTIONS - EMERGENCY RESPONSE GUIDEBOOK, GUIDE 138 (ERG, 2004)
- SMALL FIRE PRECAUTIONS - EMERGENCY RESPONSE GUIDEBOOK, GUIDE 138 (ERG, 2004)
- LARGE FIRE PRECAUTIONS - EMERGENCY RESPONSE GUIDEBOOK, GUIDE 138 (ERG, 2004)
DRY sand, dry chemical, soda ash or lime or withdraw from area and let fire burn. Move containers from fire area if you can do it without risk.
- LITHIUM OR MAGNESIUM FIRE PRECAUTIONS - EMERGENCY RESPONSE GUIDEBOOK, GUIDE 138 (ERG, 2004)
Magnesium Fires: Lithium Fires:
- TANK OR CAR/TRAILER LOAD FIRE PRECAUTIONS - EMERGENCY RESPONSE GUIDEBOOK, GUIDE 138 (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 CAS7440-09-7 (NFPA, 2002):
- Burning potassium is hard to extinguish. It burns violently, and may be accompanied by explosion and thus material dispersal and fire spreading. Water or carbon dioxide should not be used if the material is on fire or involved in a fire. Recommended extinguishing agents are dry powdered soda ash, dry graphite, powdered sodium chloride, lime, or special mixtures of dry chemicals. The material can also be smothered with dry sand, dry clay, or dry ground limestone (AAR, 2002; ITI, 1995; Lewis, 2000; NFPA, 1997; Pohanish, 2002).
- Approved Class D fire extinguishers should be used for potassium metal fires (Clare & Krenzelok, 1988; NFPA, 1997).
- Carbon dioxide, halogenated extinguishing agents, foam, or water should not be used in a fire situation involving potassium (NFPA, 1997; Pohanish, 2002).
- Water spray from a secure and explosion-proof location can be used to cool storage containers exposed to a fire hazard. If container venting sound increases in volume and pitch, discoloration of the container occurs, or if containers show any signs of deformation, cooling measures are not effective and firefighters should withdraw immediately (Pohanish, 2002).
- Employees who are part of an employer's fire brigade must be trained and equipped per 29 CFR 1910.156 (Pohanish, 2002).
Potassium is a combustible solid that can ignite spontaneously in moist air. Combustion may produce toxic gases and irritants. Combustion products include oxides (Bingham et al, 2001; NFPA, 2002; Pohanish, 2002). Toxic fumes of potassium oxide (K2O) are released when potassium metal is heated to decomposition (Lewis, 2000).
EXPLOSION HAZARD
- Potassium metal presents a serious explosion hazard, particularly due to its high and often violent reactivity with a number of substances. It reacts violently with a broad range of materials, including water and air. In some situations, certain conditions of temperature, pressure, and material state are necessary for an explosion hazard to exist. An explosion hazard can be also present during storage of potassium metal at room temperature and even when stored in mineral oil; the metal forms potassium peroxide (K2O2) and superoxide (KO3 or K2O4) which can explode on contact with organic material. Oxidized potassium metal stored under oil may also explode violently when handled or cut. The explosion is caused by interaction of residual traces of mineral oil or other organic contaminant, not the potassium metal, and is initiated by the pressure of dry cutting or impact(Bingham et al, 2001; Lewis, 2000; NFPA, 1997; Pohanish & Greene, 1997; Urben, 1999).
- Oxide-coated potassium metal presents an extremely serious and dangerous explosion hazard (Pohanish, 2002).
- A violent explosion hazard may occur with the following materials under specific conditions of temperature, pressure, and state of division (Lewis, 2000):
acetylene air (and moist air) alcohols aluminum bromide (AlBr3) ammonium nitrate + ammonium sulfate ammonium chlorocuprate ammonium bromide (NH4Br) ammonium iodide ammonium halides arsenic halides arsine (AsH3) + ammonia (NH3) Bi2O3 boric acid Boron tribromide (BBr3) carbon disulfide (impact-sensitive) solid carbon dioxide carbon monoxide chlorinated hydrocarbons halocarbons interhalogens ClO chromium trioxide (CrO3) Cu2OCl2 Cupric oxide (CuO) ethylene oxide fluorine graphite (alone, with air, or with potassium peroxide) hydrogen iodide hydrogen peroxide (H2O2) hydrogen chloride hydrazine Pb2OCl2 lead dioxide (PbO2) lead sulfate (PbSO4) maleic anhydride metal halides metal oxides nitric acid nitro en-containing explosives nonmetal halides nonmetal oxides oxalyl dihalides (including oxalyl dibromide, oxalyl dichloride) P2NF peroxides phosgene (COCl2) phosphine + ammonia (PH3 + NH3) phosphorus phosphorus pentachloride (PCl5) phosphorus tribromide (PBr3) potassium chlorocuprate potassium oxides selenium selenium oxychloride (SeOCl2) silicon tetrachloride (SiCl4) silver iodate (AgIO3) sodium iodate (NaIO3) sodium nitrite and ammonia (NaNO2 + NH3) sodium binoxide (Na2O2) tin tetraiodide + sulfur (SnI4 + S) tin dioxide (SnO2) sulfur sulfuric acid tellurium thiophosphoryl fluoride vanadyl dichloride (VOCl2) water
DUST/VAPOR HAZARD
- Dusts or mists of potassium metal cause exposure hazards, such as irritation to the eyes, nose, throat, and lungs, and higher exposure levels can lead to greater health complications and death. Prolonged exposure to fumes will also cause adverse health effects (Pohanish, 2002)
REACTIVITY HAZARD
- Potassium is one of the most reactive metals. It is a strong reducing agent and will readily react with most gases and liquids; although it does not react with the noble gases such as helium or argon. It undergoes a vigorous reaction with oxygen, water, acids, and halogens. Reaction with water is violent, generating flammable and explosive hydrogen gas and a strong caustic solution (Bingham et al, 2001; CHRIS, 2003; HSDB, 2003; Lewis, 1998; NFPA, 2002; Pohanish, 2002; Pohanish & Greene, 1997).
- A violent reaction results with oxidizers, organic materials, carbon dioxide, heavy metal compounds, carbon tetrachloride, halogenated hydrocarbons, easily oxidized materials, and many other substances. Reaction with alcohol releases hydrogen gas. Potassium metal can form unstable peroxides under normal temperature and storage conditions, or it can form potassium peroxide and superoxide. The latter materials may explode violently upon handling, including when potassium is stored under mineral oil (Ashford, 2001; Bingham et al, 2001; Pohanish, 2002; Pohanish & Greene, 1997; Urben, 1999).
- The following materials will react with potassium metal (Urben, 1999):
- Potassium reacts with (Budavari, 2001; Urben, 1999):
oxygen (vigorously) water (even at -100 degrees C) acids halogens (igniting with bromine and iodine) organic compounds containing active groups
- It will react slowly with hydrogen at 200 degrees C, and rapidly at 350-400 degrees C. At room temperature, it will react slowly with anhydrous hydrogen halides; the molten metal ignites in this reaction (Budavari, 2001).
- It will reduce (Budavari, 2001):
- The molten metal reacts with sulfur and hydrogen sulfide (Budavari, 2001).
- Reactivity may lead to a violent explosion with the following materials (under required conditions of temperature, pressure, and state of division) (Lewis, 2000; Urben, 1999):
acetylene air (and moist air) alcohols aluminum bromide (AlBr3) ammonium nitrate + ammonium sulfate ammonium chlorocuprate ammonium bromide (NH4Br) ammonium iodide ammonium halides arsenic halides arsine (AsH3) + ammonia (NH3) Bi2O3 boric acid boron tribromide (BBr3) carbon disulfide (impact-sensitive) solid carbon dioxide carbon monoxide chlorinated hydrocarbons halocarbons interhalogens ClO chromium trioxide (CrO3) Cu2OCl2 cupric oxide (CuO) ethylene oxide fluorine graphite (alone, with air, or with potassium peroxide) hydrogen halides hydrogen iodide hydrogen peroxide (H2O2) hydrogen chloride hydrazine Pb2OCl2 lead dioxide (PbO2) lead sulfate (PbSO4) maleic anhydride metal halides metal oxides nitric acid nitrogen-containing explosives non-metal halides non-metal oxides oxalyl dihalides (including oxalyl dibromide, oxalyl dichloride) P2NF peroxides phosgene (COCl2) phosphine + ammonia (PH3 + NH3) phosphorus phosphorus pentachloride (PCl5) phosphorus tribromide (PBr3) potassium chlorocuprate potassium oxides selenium selenium oxychloride (SeOCl2) silicon tetrachloride (SiCl4) silver iodate (AgIO3) sodium iodate (NaIO3) sodium nitrite and ammonia (NaNO2 + NH3) sodium binoxide (Na2O2) sulfur sulfuric acid tin tetraiodide + sulfur (SnI4 + S) tin dioxide (SnO2) tellurium thiophosphoryl fluoride vanadyl dichloride (VOCl2) water
- Hazardous reactions may occur with (Lewis, 2000; Urben, 1999):
bismuth trioxide bromine vapor carbon (e.g., soot, graphite, activated charcoal) chloride or iodide chlorine chromium trioxide copper II oxide dimethly sulfoxide ethylene oxide hydrogen bromide maleic anhydride mercury mercury II oxide molybdenum (III) oxide potassium iodide + magnesium bromide phosphorus trichloride sulfur dioxide tin (IV) oxide
- It is reported that there is risk of fire from reactivity of powdered potassium, or potassium sand, dispersed in benzene with air. Reactivity also lead to a fire when potassium was blotted with filter paper to take up solvent used in the removal of trace oil (Urben, 1999).
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 138 (ERG, 2004)
Increase, in the downwind direction, as necessary, the isolation distance of at least 50 meters (150 feet) for liquids and 25 meters (75 feet) for solids in all directions.
- FIRE - PUBLIC SAFETY EVACUATION DISTANCES - EMERGENCY RESPONSE GUIDEBOOK, GUIDE 138 (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 138 (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 the area before entry.
- Evacuate and keep people away from any spill area to avoid contact with the solid (CHRIS, 2003).
- AIHA ERPG Values for CAS7440-09-7 (AIHA, 2006):
- DOE TEEL Values for CAS7440-09-7 (U.S. Department of Energy, Office of Emergency Management, 2010):
Listed as Potassium TEEL-0 (units = mg/m3): 0.075 TEEL-1 (units = mg/m3): 0.2 TEEL-2 (units = mg/m3): 1.5 TEEL-3 (units = mg/m3): 300 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 CAS7440-09-7 (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 CAS7440-09-7 (National Institute for Occupational Safety and Health, 2007):
CONTAINMENT/WASTE TREATMENT OPTIONS
SPILL OR LEAK PRECAUTIONS - EMERGENCY RESPONSE GUIDEBOOK, GUIDE 138 (ERG, 2004) ELIMINATE all ignition sources (no smoking, flares, sparks or flames in immediate area). Do not touch or walk through spilled material. Stop leak if you can do it without risk. Use water spray to reduce vapors or divert vapor cloud drift. Avoid allowing water runoff to contact spilled material. DO NOT GET WATER on spilled substance or inside containers.
POWDER SPILL PRECAUTIONS - EMERGENCY RESPONSE GUIDEBOOK, GUIDE 138 (ERG, 2004) Cover powder spill with plastic sheet or tarp to minimize spreading and keep powder dry. DO NOT CLEAN-UP OR DISPOSE OF, EXCEPT UNDER SUPERVISION OF A SPECIALIST.
RECOMMENDED PROTECTIVE CLOTHING - EMERGENCY RESPONSE GUIDEBOOK, GUIDE 138 (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 in fire situations ONLY; it is not effective in spill situations where direct contact with the substance is possible.
In the event of a spill or release of potassium metal, immediately stop any migration of the discharged material. Ignition sources should be turned off and the fire department contacted, as well as local health, wildlife, and pollution control agencies. Water intakes and outtakes should be protected to avoid fire and explosion hazards from material contact with water, to avoid the likelihood of fire and explosion in a confined space such as a sewer, and to protect aquatic life. If the material enters a drain or outtake or potential migration to a surface water body exists, operators of nearby water intakes and any downstream water users should be contacted (CHRIS, 2003; Pohanish, 2002). If the material is not on fire and not involved in a fire (AAR, 2002): Do not use water Keep sparks, flames, and other ignition sources away. Keep material out of water sources and sewers. Keep material dry. Do not attempt to sweep up dry material.
Water should be kept away from any release of potassium. The material should be shoveled into a dry, sealed container (NFPA, 2002; Pohanish, 2002). The area of a spill should be ventilated after completion of material clean-up (Pohanish, 2002). Waste material containing potassium metal may require management as a hazardous waste. Employees involved in spill clean-up must be properly trained per OSHA requirements for hazardous waste operations and emergency response per 29 CFR 1910.120(q) , Emergency Responses to Hazardous Substances Releases (Pohanish, 2002).
Corrective response actions related to chemical or physical treatment may include neutralization (CHRIS, 2003). Potassium residues in bulk storage and processing vessels may be disposed safely using reaction with dry condensate-free steam under controlled conditions. This method is appropriate where smaller scale methods are not useful (Urben, 1999). Oxidized potassium can be destroyed by addition of tert-butanol to small portions under xylene in a hood. The material should be handled and cut under dry xylene. Scraps should be disposed in xylene by addition of tert-butanol, although use of tert-butanol can cause a violent reaction. Ethyl acetate-hydrocarbon mixtures may also be used with small quantities for disposal (Urben, 1999). 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.
Oxide-coated potassium, such as old oxidized stocks, can be destroyed through burning (Lewis, 2000; Lewis, 2001; Urben, 1999).
-ENVIRONMENTAL HAZARD MANAGEMENT
POLLUTION HAZARD
- Potassium exposure is general addressed for the anion species. It does not exist in the free form in nature, but rather it is found as the chloride in sylvite, in aluminosilicates (orthoclase and microcline), or as carnallite. Exposure to potassium metal is not common in industry, research, or academia. Releases to the environment may result from accidents during its production, handling, storage, use or storage (HSDB, 2003; Bingham et al, 2001a; Budavari, 2001).
- Welding fumes have been found to be a source of occupational exposure to potassium metal. In a study of the hazardous and toxicological aspects of potassium, it was found that improper storage or lack of appropriate precautions were the cause of most occupational exposure incidents (NIOSHTIC, 2003).
ENVIRONMENTAL FATE AND KINETICS
Potassium metal reacts vigorously with oxygen and will explode when exposed to air. It can ignite spontaneously in moist air (Budavari, 2001; Lewis, 2001; Lewis, 2000).
ABIOTIC DEGRADATION
- Release of metallic potassium to the environment will result in immediate reactivity with air or water. It spontaneously ignites or explodes upon contact with either media (Budavari, 2001; Lewis, 2000).
ENVIRONMENTAL TOXICITY
- Elemental potassium is harmful to aquatic life at very low concentrations (CHRIS, 2003).
- TLm - (freshwater) MOSQUITO FISH: 80 ppm for 24 hr (CHRIS, 2003).
-PHYSICAL/CHEMICAL PROPERTIES
MOLECULAR WEIGHT
DESCRIPTION/PHYSICAL STATE
- Elemental potassium is shiny and silver in appearance. It loses its metallic sheen and can appear silvery-white or greyish due to rapid oxidation in air. The material is odorless, soft, and waxy, and it is brittle at low temperatures. Potassium is a Group 1A alkali metal and has a body-centered cubic structure, leading to its ductility. It is the lightest metal known. Potassium is one of the most reactive and electropositive metals. The high reactivity of potassium metal contributes to its caustic and corrosive characteristics as well as its flammable and explosive properties. It presents a dangerous fire hazard, as it can ignite or explode when exposed to water or moisture and it may spontaneously ignite in air. A characteristic violet flame is emitted when potassium burns (HSDB, 2005; Ashford, 2001; Bingham et al, 2001; Budavari, 2001; Lewis, 2000; Lewis, 2001; NFPA, 2002).
VAPOR PRESSURE
- 8 mm Hg (at 432 degrees C) (Bingham et al, 2001; ILO, 1998)
SPECIFIC GRAVITY
- OTHER TEMPERATURE AND/OR PRESSURE
0.856 (at 20 degrees C) (Budavari, 2001) 0.86 (at 20 degrees C) (Bingham et al, 2001) 0.86 (at 20 degrees C; solid) (CHRIS, 2005)
- TEMPERATURE AND/OR PRESSURE NOT LISTED
0.856(ILO, 1998) 0.86 (NFPA, 2002) 0.862 (ITI, 1995)
DENSITY
- OTHER TEMPERATURE AND/OR PRESSURE
0.862 g/cm(3) (at 20 degrees C) (Lewis, 2000) 0.98 kg/l (at 20 degrees C) (Ashford, 2001)
FREEZING/MELTING POINT
63 degrees C (Bingham et al, 2001; Lewis, 2001) 63 degrees C (146 degrees F) (NFPA, 2002) 63.2 degrees C (Budavari, 2001; ILO, 1998) 63.65 degrees C (ITI, 1995; Lewis, 2000) 64 degrees C(Pohanish, 2002) 98 degrees C (Ashford, 2001)
BOILING POINT
- 760 degrees C (Ashford, 2001)
- 765.5 degrees C (Budavari, 2001; ILO, 1998)
- 766 degrees C (1410 degrees F) (NFPA, 2002)
- 770 degrees C (Bingham et al, 2001; Lewis, 2001)
- 774 degrees C (ITI, 1995; Lewis, 2000; Pohanish, 2002)
- 774 degrees C (1425 degrees F; 1047 K) (CHRIS, 2005)
FLASH POINT
- Not pertinent; combustible solid (CHRIS, 2005)
AUTOIGNITION TEMPERATURE
- 441 degrees C (Pohanish, 2002)
SOLUBILITY
Solubility in water (at 68 degrees F): Reacts (Bingham et al, 2001). Decomposes in water (Bingham et al, 2001; NFPA, 2002).
Soluble in aniline (Lewis, 2001). Soluble in ethylenediamine and aniline (Budavari, 2001).
Soluble in liquid ammonia (NH3) or blue-black solution (Lewis, 2000). Soluble in liquid ammonia and in several metals (Budavari, 2001). Soluble in liquid ammonia, mercury, and sodium (Lewis, 2001). Soluble in liquid ammonia (Ashford, 2001). Soluble in acid and mercury (HSDB, 2005).
OTHER/PHYSICAL
-REFERENCES
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