PHOSPHORUS, RED
HAZARDTEXT ®
Information to help in the initial response for evaluating chemical incidents
-IDENTIFICATION
SYNONYMS
IDENTIFIERS
1338-Red phosphorus, amorphous 1338-Red phosphorus 1338-Phosphorus, amorphous, red
SYNONYM REFERENCE
- (CHRIS , 1991; EPA, 1985; HSDB , 1991; RTECS , 1991; Sax & Lewis, 1989; NFPA, 1991)
USES/FORMS/SOURCES
Red phosphorus is used in pyrotechnics; in the manufacture of safety matches; in organic synthesis; in the manufacture of phosphoric acid, phosphine, phosphoric anhydride, phosphorus pentachloride, and phosphorus trichloride; and, in the manufacture of fertilizers, pesticides, incendiary shells, smoke bombs, and tracer bullets (Budavari, 1989).
Phosphorus exists in three main allotropic forms: white, black, and red. The same liquid is obtained on melting. Phosphorus atoms exist as symmetrical, tetrahedral P(4) molecules in the liquid phase and in the vapor phase below 800 degrees C; molecules dissociate to P(2) above 800 degrees C (Budavari, 1989). Red phosphorus is a red to violet powder and sublimes at 416 degrees C (Budavari, 1989). Red phosphorus is insoluble, unabsorbable, and nontoxic, unless it contains the white form as an impurity.
-CLINICAL EFFECTS
GENERAL CLINICAL EFFECTS
- Red phosphorus is insoluble, unabsorbable, and nontoxic, unless it contains the white form as an impurity. Red phosphorus may form the more hazardous white phosphorus at high temperatures.
- POTENTIAL HEALTH HAZARDS - EMERGENCY RESPONSE GUIDEBOOK, GUIDE 133 (ERG, 2004)
Fire may produce irritating and/or toxic gases. Contact may cause burns to skin and eyes. Contact with molten substance may cause severe burns to skin and eyes. Runoff from fire control may cause pollution.
-MEDICAL TREATMENT
LIFE SUPPORT
- Support respiratory and cardiovascular function.
SUMMARY
- FIRST AID - EMERGENCY RESPONSE GUIDEBOOK, GUIDE 133 (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. Removal of solidified molten material from skin requires medical assistance. Keep victim warm and quiet. Ensure that medical personnel are aware of the material(s) involved and take precautions to protect themselves.
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.
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). If White Phosphorus is believed to be present, as judged by spontaneous oxidation (smoking) of tissue, refer to Phosphorus, White Hazardtext(R) Management.
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 - GASTRIC LAVAGE - Although gastric lavage with a 1:5,000 solution of potassium permanganate has been recommended to convert phosphorus to less harmful oxidation products (Chretien, 1945), there are no data documenting efficacy. 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. Red phosphorus in insoluble and relatively non-toxic. No GI decontamination is necessary unless the more toxic whit phosphorus as an impurity.
-RANGE OF TOXICITY
MINIMUM LETHAL EXPOSURE
MAXIMUM TOLERATED EXPOSURE
- Carcinogenicity Ratings for CAS7723-14-0 :
ACGIH (American Conference of Governmental Industrial Hygienists, 2010): Not Listed EPA (U.S. Environmental Protection Agency, 2011): D ; Listed as: White phosphorus 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: Phosphorus (yellow) 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 CAS7723-14-0 (U.S. Environmental Protection Agency, 2011):
Oral: Slope Factor: RfD: 2x10(-5) mg/kg-day
Inhalation: Drinking Water:
-STANDARDS AND LABELS
WORKPLACE STANDARDS
- ACGIH TLV Values for CAS7723-14-0 (American Conference of Governmental Industrial Hygienists, 2010):
- AIHA WEEL Values for CAS7723-14-0 (AIHA, 2006):
- NIOSH REL and IDLH Values for CAS7723-14-0 (National Institute for Occupational Safety and Health, 2007):
- OSHA PEL Values for CAS7723-14-0 (U.S. Occupational Safety, and Health Administration (OSHA), 2010):
- OSHA List of Highly Hazardous Chemicals, Toxics, and Reactives for CAS7723-14-0 (U.S. Occupational Safety and Health Administration, 2010):
ENVIRONMENTAL STANDARDS
- EPA CERCLA, Hazardous Substances and Reportable Quantities for CAS7723-14-0 (U.S. Environmental Protection Agency, 2010):
- EPA CERCLA, Hazardous Substances and Reportable Quantities, Radionuclides for CAS7723-14-0 (U.S. Environmental Protection Agency, 2010):
- EPA RCRA Hazardous Waste Number for CAS7723-14-0 (U.S. Environmental Protection Agency, 2010b):
- EPA SARA Title III, Extremely Hazardous Substance List for CAS7723-14-0 (U.S. Environmental Protection Agency, 2010):
Listed as: Phosphorus Reportable Quantity, in pounds: 1 Threshold Planning Quantity, in pounds: Note(s): a a: This material is a reactive solid. The TPQ does not default to 10,000 pounds for non-powder, non-molten, non-solution form. d: Revised TPQ based on new or re-evaluated toxicity data, April 22, 1987.
- EPA SARA Title III, Community Right-to-Know for CAS7723-14-0 (40 CFR 372.65, 2006; 40 CFR 372.28, 2006):
Listed as: Phosphorus (yellow or white) Effective Date for Reporting Under 40 CFR 372.30: 1/1/87 Lower Thresholds for Chemicals of Special Concern under 40 CFR 372.28:
- DOT List of Marine Pollutants for CAS7723-14-0 (49 CFR 172.101 - App. B, 2005):
Listed as White phosphorus, dry Severe Marine Pollutant: Yes Listed as White phosphorus, wet Severe Marine Pollutant: Yes Listed as Yellow phosphorus, dry Severe Marine Pollutant: Yes Listed as Yellow phosphorus, wet Severe Marine Pollutant: Yes Listed as Phosphorus white, or yellow, molten Severe Marine Pollutant: Yes Listed as Phosphorus, white or yellow dry or under water or in solution Severe Marine Pollutant: Yes Listed as Phosphorus, white, molten Severe Marine Pollutant: Yes Listed as Phosphorus, yellow, molten Severe Marine Pollutant: Yes
- EPA TSCA Inventory for CAS7723-14-0 (EPA, 2005):
SHIPPING REGULATIONS
- DOT -- Table of Hazardous Materials and Special Provisions for UN/NA Number 1338 (49 CFR 172.101, 2005):
- ICAO International Shipping Name for UN1338 (ICAO, 2002):
LABELS
- NFPA Hazard Ratings for CAS7723-14-0 (NFPA, 2002):
-PERSONAL PROTECTION
SUMMARY
- RECOMMENDED PROTECTIVE CLOTHING - EMERGENCY RESPONSE GUIDEBOOK, GUIDE 133 (ERG, 2004)
- Wear positive pressure breathing apparatus and full protective clothing.
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 7723-14-0.
-PHYSICAL HAZARDS
FIRE HAZARD
- FLAMMABILITY CLASSIFICATION
- NFPA Flammability Rating for CAS7723-14-0 (NFPA, 2002):
- FIRE CONTROL/EXTINGUISHING AGENTS
- SMALL FIRE PRECAUTIONS - EMERGENCY RESPONSE GUIDEBOOK, GUIDE 133 (ERG, 2004)
Dry chemical, CO2, sand, earth, water spray or regular foam.
- LARGE FIRE PRECAUTIONS - EMERGENCY RESPONSE GUIDEBOOK, GUIDE 133 (ERG, 2004)
- TANK OR CAR/TRAILER LOAD FIRE PRECAUTIONS - EMERGENCY RESPONSE GUIDEBOOK, GUIDE 133 (ERG, 2004)
Cool containers with flooding quantities of water until well after fire is out. For massive fire, use unmanned hose holders or monitor nozzles; if this is impossible, withdraw from area and let fire burn. 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 CAS7723-14-0 (NFPA, 2002):
- Flood with water to control flames, then smother with wet sand, clay, ground limestone. Approach fire from upwind to avoid hazardous vapors and toxic decomposition products. Where access to the area is strictly controlled, it may be best to allow the release to burn itself out. Fire situations may require evacuation. Fight fire from protected location or maximum possible distance (NFPA, 1991).
Combustion by-products of red phosphorus include oxides of phosphorus, phosphine, and phosphoric acid if water is present (NFPA, 1991). Red phosphorus may decompose at 554 degrees F (290 degrees C) into the more hazardous white or yellow phosphorus (NFPA, 1991). Refer to the PHOSPHORUS, WHITE HAZARDTEXT management for more information.
EXPLOSION HAZARD
- Avoid contact with KClO3, KMnO4, peroxides and other oxidizing agents; explosions may result on contact or friction (Budavari, 1989).
- Phosphorus may explode on contact with oxidizing materials (NFPA, 1991).
DUST/VAPOR HAZARD
- Combustion by-products of red phosphorus include oxides of phosphorus, phosphine, and phosphoric acid if water is present (NFPA, 1991).
REACTIVITY HAZARD
- Very reactive. Fire and explosive hazard when in contact with oxidizing materials. When in contact with alkali, phosphine gas may be produced. Vigorously reacts with cesium, lithium, potassium, rubidium, sodium, and sulfur. Explodes with ammonium nitrate and moist chlorates. Burns spontaneously or explodes with chlorine, fluorine, or bromine. May explode with nitrates, nitrogen bromide, or selenium monochloride, selenium oxyfluoride, or selenium tetrafluoride.
- Red phosphorus catches fire when heated in air to about 260 degrees C and burns with formation of the pentoxide (Budavari, 1989).
- Red phosphorus burns when heated in an atmosphere of chlorine (Budavari, 1989).
- Red phosphorus will not ignite spontaneously but may be ignited by friction, static electricity, or heating or oxidizing agents. (Clayton & Clayton, 1981).
- Red phosphorus yields the white modification when distilled at 290 degrees C (Budavari, 1989).
- Avoid contact with KClO3, KMnO4, peroxides and other oxidizing agents; explosions may result on contact or friction (Budavari, 1989).
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 133 (ERG, 2004)
- FIRE - PUBLIC SAFETY EVACUATION DISTANCES - EMERGENCY RESPONSE GUIDEBOOK, GUIDE 133 (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 133 (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 25 meters (75 feet) in all directions. Keep unauthorized personnel away. Stay upwind. Keep out of low areas.
- AIHA ERPG Values for CAS7723-14-0 (AIHA, 2006):
- DOE TEEL Values for CAS7723-14-0 (U.S. Department of Energy, Office of Emergency Management, 2010):
Listed as Phosphorus (red) TEEL-0 (units = mg/m3): 0.05 TEEL-1 (units = mg/m3): 0.4 TEEL-2 (units = mg/m3): 3 TEEL-3 (units = mg/m3): 4 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 CAS7723-14-0 (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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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 CAS7723-14-0 (National Institute for Occupational Safety and Health, 2007):
IDLH: 5 mg/m3 Note(s): Not Listed
CONTAINMENT/WASTE TREATMENT OPTIONS
SPILL OR LEAK PRECAUTIONS - EMERGENCY RESPONSE GUIDEBOOK, GUIDE 133 (ERG, 2004) ELIMINATE all ignition sources (no smoking, flares, sparks or flames in immediate area). Do not touch or walk through spilled material.
RECOMMENDED PROTECTIVE CLOTHING - EMERGENCY RESPONSE GUIDEBOOK, GUIDE 133 (ERG, 2004) 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 , 1991). Prompt cleanup and removal are necessary. Shovel into suitable dry container. Control runoff and isolate discharged material for proper disposal. Report any release in excess of 1 pound (NFPA, 1991). ENVIRONMENTAL CONSIDERATIONS - LAND SPILL (AAR, 1987) Dig a pit, pond, lagoon, holding area to contain liquid or solid material. Cover solids with a plastic sheet to prevent dissolving in rain or fire fighting water.
ENVIRONMENTAL CONSIDERATIONS - WATER SPILL (AAR, 1987) Use natural deep water pockets, excavated lagoons, or sand bag barriers to trap material at bottom. Remove trapped material with suction hoses. Use mechanical dredges or lifts to remove immobilized masses of pollutants and precipitates.
STORAGE Red phosphorus will not ignite spontaneously but may be ignited by friction, static electricity, or heating or oxidizing agent. Handling it in an aqueous solution helps prevent fires (Clayton & Clayton, 1981). Store red phosphorus in a cool, dry place with adequate ventilation and avoid overheating. Separate from oxidizing materials. Always keep container closed (HSDB , 1991; NFPA, 1991).
A laboratory scale reactor, consisting of zinc chloride activated nutshell charcoal, was setup to adsorb phosphate ions from waste water. The highest value phosphate adsorption, from a 4 g per liter solution, was 57% for an adsorbent particle size of 106.1 mu per meter (Bhargava & Sheldarkar, 1992).
-ENVIRONMENTAL HAZARD MANAGEMENT
POLLUTION HAZARD
- This study suggests that there is a seasonal shift from Phosphorus (P) to Nitrogen (N) as the limiting nutrient to biomass accumulation in Chesapeake Bay. The results of the study showed that in winter and spring, P limits phytoplankton growth rates; while in summer N limits the algal accumulation (Fisher et al, 1992).
- A study evaluated the transport and transformation of phosphorus (P) in the Atlantic coastal plain. The distribution and fractionation of P in forested and agricultural soils in the Rhodes River watershed was the subject of the study. About 70% of the P in forest soils was bound in organic forms. It was found that particulate P dominated the export of phosphorus from both watersheds (Vaithiyanathan & Correll, 1992).
- A laboratory study evaluated the effect of sesquioxidic gravels on phosphorus sorption by lateritic soils. The phosphorus content was monitored by X-ray diffraction, autoradiography, and electron microscopy. Phosphorus adsorption increased as the gravel content of the soil and gravel particle size increased. The study concluded that both the phosphorus requirements of the plants and the gravel content of the soil need to be assessed when planning fertilizer strategy (Weaver et al, 1992).
- The phosphate adsorption characteristics of several clay-containing soils were measured in a research study. Standard isotherms were measured using a solution concentration of 1 milligram of phosphorus per liter, resulting in an equilibrium adsorption range after 75 days of between 1.62 and 3.18 mcmol P/m(2) (Torrent et al, 1992).
- Adsorption isotherms were measured for sulfate and phosphate ions on soil that had been incubated with lime. The lime treatment affected sulfate ions more strongly than phosphate ions. The results suggested that sulfate should be less mobile in alkaline soils (Marsh et al, 1992).
- A laboratory study using a flow (miscible displacement) reactor was used to evaluate the effects of electrolyte concentration and exchangeable sodium (sodicity) on the solubility of phosphorus in soils. The results showed that increasing sodium concentration made the weakly adsorbed phosphorus more labile and thus may have an important bearing on the phosphorus nutrition of crops (Curtin et al, 1992).
- TRANSPORT FROM SEDIMENTS: Sediments were analyzed for potentially available phosphorus and total phosphorus (TP). Water from the same location was analyzed for dissolved phosphorus and TP. A negative correlation was found between the observed flow and the water TP concentration. The results suggested that sediments may be a significant source of dissolved phosphorus (Rosensteel & Strom, 1992).
- Phosphorus does not occur free in nature. It is found in the form of phosphates in the minerals chlorapatite, fluorapatite, vivianite, wavellite and "phosphate rock" or phosphorite; occurs in small quantities in granite rocks; occurs in all fertile soil; and, is an essential constituent of protoplasm, nervous tissue and bones. Its abundance in the earth's crust is about 0.12 percent (Budavari, 1989).
- Fifty-nine elements, PCBs, volatile N-nitrosamines and gamma emission were determined in 30 sewage sludges from 23 American cities. Phosphorus concentration in sludges, determined by emission spectrometry, ranged from 0.27 to 3.2% dry weight (HSDB , 1991).
ENVIRONMENTAL FATE AND KINETICS
OTHER In a study of metal levels at various trophic levels within an undisturbed Precambrian Shield lake ecosystem, concentrations of 21 naturally occurring elements including phosphorus were measured in sediments, clams, fish, birds, and mammals. Mercury was the only element to exhibit biomagnification (HSDB , 1991). Macronutrient and trace metal content was determined in reindeer lichens (Cladonia cladina) from 23 bogs; C. arbuscula was sampled from 20 localities, C. stellaris (C. alpestris) from 12 and C. mitis from 2. Calculated on the basis of the total atmospheric fallout in the region, the annual retention percentages in the Cladonis carpets were 124 percent for phosphorus. Apparently there is a significant active uptake of phosphorus; it is chiefly accumulated in the living top part (HSDB , 1991).
ENVIRONMENTAL TOXICITY
- Prairie dogs and rock doves were exposed to red phosphorus/butyl rubber smoke. The animals were subjected to multiple applications of smoke in concentrations of 0.0, 1.0, and 4.0 gm/L. Four daily 80-min smoke exposures had no significant effect on the prairie dogs. The rock doves responded to two daily doses with elevated respiratory frequency in two males followed by death. These results showed that rock doves are more susceptible to red phosphorus/butyl rubber smoke than prairie dogs, but it is unlikely that the smoke poses a significant risk to either species under field conditions (Johns et al, 1992).
-PHYSICAL/CHEMICAL PROPERTIES
MOLECULAR WEIGHT
DESCRIPTION/PHYSICAL STATE
- Red phosphorus is a red to violet, odorless powder. Red phosphorus sublimes at 416 degrees C (Budavari, 1989).
- Phosphorus exists in three main allotropic forms: red, white, and black. The same liquid is obtained on melting. Phosphorus atoms exist as symmetrical, tetrahedral P(4) molecules in the liquid phase and in the vapor phase below 800 degrees C; molecules dissociate to P(2) above 800 degrees C (Budavari, 1989).
- White phosphorus is a colorless or white, transparent, crystalline solid with a waxy appearance and a distinct garlic-like odor. It darkens on exposure to light (Budavari, 1989).
White phosphorus is sometimes called yellow phosphorus due to its color from impurities. When exposed to air in the dark, white phosphorus emits a greenish light and gives off white fumes (Budavari, 1989).
- White phosphorus sublimes in a vacuum at ordinary temperature when exposed to light (Budavari, 1989).
- Black phosphorus is polymorphic. The orthorhombic crystalline form is stable in air, resembles graphite in texture, and is produced from white phosphorus under high pressure. Amorphous black phosphorus is prepared at lower pressures. At higher pressure the orthorhombic form undergoes reversible transition to a rhombohedral structure and a cubic structure (Budavari, 1989).
DENSITY
- TEMPERATURE AND/OR PRESSURE NOT LISTED
FREEZING/MELTING POINT
BOILING POINT
- 280 degrees C (Budavari, 1989)
AUTOIGNITION TEMPERATURE
- 500 degrees F in air (Sax & Lewis, 1989)
SOLUBILITY
Red phosphorus is soluble in phosphorus tribromide and insoluble in organic solvents (Budavari, 1989). Red phosphorus is soluble in absolute alcohol, carbon disulfide, ether, and ammonia (HSDB , 1991).
-REFERENCES
GENERAL BIBLIOGRAPHY- 40 CFR 372.28: Environmental Protection Agency - Toxic Chemical Release Reporting, Community Right-To-Know, Lower thresholds for chemicals of special concern. National Archives and Records Administration (NARA) and the Government Printing Office (GPO). Washington, DC. Final rules current as of Apr 3, 2006.
- 40 CFR 372.65: Environmental Protection Agency - Toxic Chemical Release Reporting, Community Right-To-Know, Chemicals and Chemical Categories to which this part applies. National Archives and Records Association (NARA) and the Government Printing Office (GPO), Washington, DC. Final rules current as of Apr 3, 2006.
- 49 CFR 172.101 - App. B: Department of Transportation - Table of Hazardous Materials, Appendix B: List of Marine Pollutants. National Archives and Records Administration (NARA) and the Government Printing Office (GPO), Washington, DC. Final rules current as of Aug 29, 2005.
- 49 CFR 172.101: Department of Transportation - Table of Hazardous Materials. National Archives and Records Administration (NARA) and the Government Printing Office (GPO), Washington, DC. Final rules current as of Aug 11, 2005.
- 62 FR 58840: Notice of the National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances - Proposed AEGL Values, Environmental Protection Agency, NAC/AEGL Committee. National Archives and Records Administration (NARA) and the Government Publishing Office (GPO), Washington, DC, 1997.
- 65 FR 14186: Notice of the National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances - Proposed AEGL Values, Environmental Protection Agency, NAC/AEGL Committee. National Archives and Records Administration (NARA) and the Government Publishing Office (GPO), Washington, DC, 2000.
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