CHROMIC SULFATE
HAZARDTEXT ®
Information to help in the initial response for evaluating chemical incidents
-IDENTIFICATION
SYNONYMS
IDENTIFIERS
Editor's Note: This material is not listed in the Emergency Response Guidebook. Based on the material's physical and chemical properties, toxicity, or chemical group, a guide has been assigned. For additional technical information, contact one of the emergency response telephone numbers listed under Public Safety Measures.
SYNONYM REFERENCE
USES/FORMS/SOURCES
Chromic sulfate is used in the insolubilization of gelatin; in catalyst preparations; as mordant in the textile industry; in the tanning of leather; in chrome plating; in the manufacture of Cr, CrO3, and Cr alloys; to improve the dispersibility of vinyl polymers in water; and in the manufacture of green varnishes, paints, inks and glazes for porcelain (Budavari, 1989).
Chromic sulfate is a peach-colored, odorless solid (Budavari, 1989; CHRIS , 1991). Hydrates are known in both green and violet modifications, and have several degrees of hydration up to 18H2O (Budavari, 1989).
-CLINICAL EFFECTS
GENERAL CLINICAL EFFECTS
- Oral ingestion produces gastrointestinal corrosion and acute multi-system shock, followed by renal failure, hemorrhagic diathesis, and hepatic injury within several days.
- Inhalation may cause corrosive action on mucous membranes. Dermal exposure may elicit an allergic reaction. Corrosive action on skin. Lesions are confined to exposed parts.
- Chromic sulfate is irritating to the skin, eyes, respiratory tract and mucous membranes.
- Chromic sulfate is moderately toxic to humans. Between 1 ounce and 1 pound may be fatal. Chromic sulfate has a low toxicity when compared to chromate and dichromate salts.
- Chromate salts are suspected carcinogens of the lungs, nasal cavity and paranasal sinus. They are also experimental carcinogens of the stomach and larynx.
- POTENTIAL HEALTH HAZARDS - EMERGENCY RESPONSE GUIDEBOOK, GUIDE 171 (ERG, 2004)
Inhalation of material may be harmful. Contact may cause burns to skin and eyes. Inhalation of Asbestos dust may have a damaging effect on the lungs. Fire may produce irritating, corrosive and/or toxic gases. Some liquids produce vapors that may cause dizziness or suffocation. Runoff from fire control may cause pollution.
-MEDICAL TREATMENT
LIFE SUPPORT
- Support respiratory and cardiovascular function.
SUMMARY
- FIRST AID - EMERGENCY RESPONSE GUIDEBOOK, GUIDE 171 (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. Ensure that medical personnel are aware of the material(s) involved, and take precautions to protect themselves.
-RANGE OF TOXICITY
MINIMUM LETHAL EXPOSURE
The minimum lethal human dose to this agent has not been delineated. Chromic sulfate is moderately toxic to humans. Between 1 ounce and 1 pound may be fatal. Chromic sulfate has a low toxicity when compared to chromate and dichromate salts (OHM/TADS , 1991).
MAXIMUM TOLERATED EXPOSURE
- Carcinogenicity Ratings for CAS10101-53-8 :
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 CAS10101-53-8 (U.S. Environmental Protection Agency, 2011):
-STANDARDS AND LABELS
WORKPLACE STANDARDS
- ACGIH TLV Values for CAS10101-53-8 (American Conference of Governmental Industrial Hygienists, 2010):
- AIHA WEEL Values for CAS10101-53-8 (AIHA, 2006):
- NIOSH REL and IDLH Values for CAS10101-53-8 (National Institute for Occupational Safety and Health, 2007):
- OSHA PEL Values for CAS10101-53-8 (U.S. Occupational Safety, and Health Administration (OSHA), 2010):
- OSHA List of Highly Hazardous Chemicals, Toxics, and Reactives for CAS10101-53-8 (U.S. Occupational Safety and Health Administration, 2010):
ENVIRONMENTAL STANDARDS
- EPA CERCLA, Hazardous Substances and Reportable Quantities for CAS10101-53-8 (U.S. Environmental Protection Agency, 2010):
- EPA CERCLA, Hazardous Substances and Reportable Quantities, Radionuclides for CAS10101-53-8 (U.S. Environmental Protection Agency, 2010):
- EPA RCRA Hazardous Waste Number for CAS10101-53-8 (U.S. Environmental Protection Agency, 2010b):
- EPA SARA Title III, Extremely Hazardous Substance List for CAS10101-53-8 (U.S. Environmental Protection Agency, 2010):
- EPA SARA Title III, Community Right-to-Know for CAS10101-53-8 (40 CFR 372.65, 2006; 40 CFR 372.28, 2006):
- DOT List of Marine Pollutants for CAS10101-53-8 (49 CFR 172.101 - App. B, 2005):
- EPA TSCA Inventory for CAS10101-53-8 (EPA, 2005):
SHIPPING REGULATIONS
- DOT -- Table of Hazardous Materials and Special Provisions (49 CFR 172.101, 2005):
- ICAO International Shipping Name (ICAO, 2002):
LABELS
- NFPA Hazard Ratings for CAS10101-53-8 (NFPA, 2002):
-PERSONAL PROTECTION
SUMMARY
- RECOMMENDED PROTECTIVE CLOTHING - EMERGENCY RESPONSE GUIDEBOOK, GUIDE 171 (ERG, 2004)
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 10101-53-8.
-PHYSICAL HAZARDS
FIRE HAZARD
Editor's Note: This material is not listed in the Emergency Response Guidebook. Based on the material's physical and chemical properties, toxicity, or chemical group, a guide has been assigned. For additional technical information, contact one of the emergency response telephone numbers listed under Public Safety Measures. POTENTIAL FIRE OR EXPLOSION HAZARDS - EMERGENCY RESPONSE GUIDEBOOK, GUIDE 171 (ERG, 2004) Some may burn but none ignite readily. Containers may explode when heated. Some may be transported hot.
- FLAMMABILITY CLASSIFICATION
- NFPA Flammability Rating for CAS10101-53-8 (NFPA, 2002):
- FIRE CONTROL/EXTINGUISHING AGENTS
- SMALL FIRE PRECAUTIONS - EMERGENCY RESPONSE GUIDEBOOK, GUIDE 171 (ERG, 2004)
- LARGE FIRE PRECAUTIONS - EMERGENCY RESPONSE GUIDEBOOK, GUIDE 171 (ERG, 2004)
Water spray, fog or regular foam. Move containers from fire area if you can do it without risk. Do not scatter spilled material with high pressure water streams. Dike fire-control water for later disposal.
- TANK FIRE PRECAUTIONS - EMERGENCY RESPONSE GUIDEBOOK, GUIDE 171 (ERG, 2004)
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 CAS10101-53-8 (NFPA, 2002):
DUST/VAPOR HAZARD
- When heated, chromic sulfate decomposes to chromic acid (HSDB , 1991).
REACTIVITY HAZARD
- When heated, chromic sulfate decomposes to chromic acid (HSDB , 1991).
- Chromic sulfate is potentially incompatible with strong oxidizers (HSDB , 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 171(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 171 (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 171 (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.
- AIHA ERPG Values for CAS10101-53-8 (AIHA, 2006):
- DOE TEEL Values for CAS10101-53-8 (U.S. Department of Energy, Office of Emergency Management, 2010):
Listed as Chromic sulfate (Chromium(III) sulfate (2:3) TEEL-0 (units = mg/m3): 1.89 TEEL-1 (units = mg/m3): 5.66 TEEL-2 (units = mg/m3): 9.43 TEEL-3 (units = mg/m3): 94.3 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 CAS10101-53-8 (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 CAS10101-53-8 (National Institute for Occupational Safety and Health, 2007):
CONTAINMENT/WASTE TREATMENT OPTIONS
SPILL OR LEAK PRECAUTIONS - EMERGENCY RESPONSE GUIDEBOOK, GUIDE 171 (ERG, 2004) Do not touch or walk through spilled material. Stop leak if you can do it without risk. Prevent dust cloud. Avoid inhalation of asbestos dust.
RECOMMENDED PROTECTIVE CLOTHING - EMERGENCY RESPONSE GUIDEBOOK, GUIDE 171 (ERG, 2004) At the time of this review, criteria for land treatment of 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). ENVIRONMENTAL CONSIDERATIONS - LAND SPILL (AAR, 1987) Dig a pit, pond, lagoon, or 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) Neutralize with agricultural lime (CaO), crushed limestone (CaCO3), or sodium bicarbonate (NaHCO3). Adjust pH to neutral (Ph = 7). Use mechanical dredges or lifts to remove immobilized masses of pollutants and precipitates.
SMALL SPILL PRECAUTIONS - EMERGENCY RESPONSE GUIDEBOOK, GUIDE 171 (ERG, 2004) SMALL DRY SPILL PRECAUTIONS - EMERGENCY RESPONSE GUIDEBOOK, GUIDE 171 (ERG, 2004)
-ENVIRONMENTAL HAZARD MANAGEMENT
POLLUTION HAZARD
- The following information on pollution hazard is for chromium in general.
- Chromium is widely distributed; the average concentration is 125 mg/kg in the continental crust. It is present in minor amounts in igneous rocks and is much more abundant in basic and ultrabasic types of rocks than in the more silicic types of rocks. Chromium is rare in natural waters (HSDB , 1991).
- Chromium is present in small quantities in all soils and plants. It is considered agriculturally as a deleterious element. Certain soils with a relatively high content (0.2 to 0.4%) are said to be infertile (HSDB , 1991).
However, many fertilizers contain appreciable amounts of chromium (from less than 5 to 3,000 ppm) (HSDB , 1991).
- The two largest artificial sources of chromium emission in the atmosphere are from the chemical manufacturing industry and from combustion of natural gas, oil and coal (HSDB , 1991).
- The concentration of chromium in United States river waters usually ranges between 1 and 30 mcg/L. The higher values of chromium can be related to sources of anthropogenic pollution. In ocean water, the mean chromium concentration is lower than in river water, with a value of 0.3 mcg/L, and a range of 0.2 to 50 mcg/L (HSDB , 1991).
- In a 1987 study of 3,834 US tap waters, the concentration of chromium ranged from 0.4 to 8.0 mcg/L. The reported chromium concentrations in the study may be somewhat higher than the actual values due to inadequate flushing of tap water before collection of samples (HSDB , 1991).
- A 1987 study of different kinds of soils from 20 sites reported chromium concentrations ranging from 4.9 to 71 mg/kg (HSDB , 1991).
- The atmospheric chromium concentration in the U.S. is typically less than 0.01 mcg/m(3) in rural areas and 0.01 mcg/m(3) in urban areas (HSDB , 1991).
ENVIRONMENTAL FATE AND KINETICS
OTHER The following information on environmental kinetics is for chromium in general. TERRESTRIAL FATE: Most soil chromium is in mineral, absorbed, or precipitated form. Chromium probably occurs as the insoluble chromium(III) oxide in soil, as the organic matter in soil is expected to reduce any soluble chromate to insoluble chromic oxide (HSDB , 1991). Chromium in soil can be transported to the atmosphere by way of aerosol formation. Chromium is also transported from soil through runoff and leaching of water. Runoff could remove both chromium ions and bulk precipitates of chromium, with final deposition on either a different land area or a water body. In addition, flooding of soils and the subsequent anaerobic decomposition of plant matter may increase dissolution of chromium(III) oxides in the soil (HSDB , 1991). Uptake is greater from ultrabasic soils by a factor of 5 to 40 than on calcarious or silica-based soils (HSDB , 1991). Soil pH is a major determinant of uptake. Plant damage to crops may result from levels above 0.5 ppm as free ion in the soil solution. An apparent threshold effect has also been noted, but not quantified. Toxic crops from uptake can be avoided by keeping the concentration below 164 ppm in the top 12 inches of soil (OHM/TADS , 1991).
AQUATIC FATE: Most of the chromium in surface waters may be present in particulate form as sediment. Some of the particulate chromium would remain as suspended matter and ultimately be deposited in sediments. The exact chemical forms of chromium in surface waters are not well defined (HSDB , 1991). Although most of the soluble chromium in surface waters may be present as chromium(VI), a small amount may be present as chromium(III) organic complexes. Hexavalent chromium is the major stable form of chromium in seawater; however, chromium(VI) may be reduced to chromium(III) by organic matter present in water, and may eventually deposit in sediments (HSDB , 1991). Because there are no known chromium compounds that can volatilize from water, transport of chromium from water to the atmosphere is not likely other than by transport by windblown sea sprays (HSDB , 1991).
ATMOSPHERIC FATE: Under normal conditions, chromium(III) and chromium(0) are relatively unreactive in the atmosphere. Chromium(VI) in air may react with particulate matter or gaseous pollutants to form chromium(III). However, these atmospheric reactions have not been extensively studied (HSDB , 1991). Chromium is removed from air through wet and dry depositions. The total yearly deposition of chromium in urban areas may vary from 0.12 mcg/m(2) to 3 mcg/m(2). In general, urban areas have higher total deposition than rural areas. Chromium concentration in a wet deposition may vary from 0.004 to 0.060 mcg/Ml and 0.0006 to 0.034 mcg/L for urban and rural areas, respectively. The precipitated chromium from the air enters surface water or soil (HSDB , 1991). By analogy with the residence time of atmospheric copper, the residence time of atmospheric chromium is expected to be less than 10 days (HSDB , 1991).
Generally, there is little tendency for chromium to accumulate along food chains in the trivalent inorganic form (HSDB , 1991).
ENVIRONMENTAL TOXICITY
- The lethal concentration of chromium sulfate to stickelbacks is 1.2 mg/L. The fish critical concentration is 1 mg/L (CHRIS , 1991).
- The aquatic toxicity of chromium sulfate to bluegill sunfish is estimated to be 35 ppm, based on 17.7 ppm/96H/LC50 for chromic acid (OHM/TADS , 1991).
- Ecotoxicity Values (HSDB , 1991):
-PHYSICAL/CHEMICAL PROPERTIES
MOLECULAR WEIGHT
DESCRIPTION/PHYSICAL STATE
- Chromic sulfate is a peach-colored, odorless solid (CHRIS, 2005; Budavari, 1989) . Hydrates are known in both green and violet modifications, and have several degrees of hydration up to 18 H2O. The hydrated technical product comes in the form of a finely granular, dark-green flake or powder (Budavari, 1989).
PH
VAPOR PRESSURE
DENSITY
- TEMPERATURE AND/OR PRESSURE NOT LISTED
FREEZING/MELTING POINT
BOILING POINT
FLASH POINT
EXPLOSIVE LIMITS
SOLUBILITY
Chromic sulfate is practically insoluble in water (Budavari, 1989). Hydrated technical product: readily soluble in water (Budavari, 1989).
-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.
- 65 FR 39264: 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.
- 65 FR 77866: 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.
- 66 FR 21940: 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, 2001.
- 67 FR 7164: 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, 2002.
- 68 FR 42710: 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, 2003.
- 69 FR 54144: 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, 2004.
- AIHA: 2006 Emergency Response Planning Guidelines and Workplace Environmental Exposure Level Guides Handbook, American Industrial Hygiene Association, Fairfax, VA, 2006.
- American Conference of Governmental Industrial Hygienists : ACGIH 2010 Threshold Limit Values (TLVs(R)) for Chemical Substances and Physical Agents and Biological Exposure Indices (BEIs(R)), American Conference of Governmental Industrial Hygienists, Cincinnati, OH, 2010.
- Budavari S: The Merck Index, 11th ed, Merck & Co, Inc, Rahway, NJ, 1989, pp 346.
- Burgess JL, Kirk M, Borron SW, et al: Emergency department hazardous materials protocol for contaminated patients. Ann Emerg Med 1999; 34(2):205-212.
- CHRIS : CHRIS Hazardous Chemical Data. US Department of Transportation, US Coast Guard. Washington, DC (Internet Version). Edition expires 1991; provided by Truven Health Analytics Inc., Greenwood Village, CO.
- CHRIS: CHRIS Hazardous Chemical Data. US Department of Transportation, US Coast Guard. Washington, DC (Internet Version). Edition expires 2005; provided by Truven Health Analytics Inc., Greenwood Village, CO.
- DFG: List of MAK and BAT Values 2002, Report No. 38, Deutsche Forschungsgemeinschaft, Commission for the Investigation of Health Hazards of Chemical Compounds in the Work Area, Wiley-VCH, Weinheim, Federal Republic of Germany, 2002.
- EPA: Search results for Toxic Substances Control Act (TSCA) Inventory Chemicals. US Environmental Protection Agency, Substance Registry System, U.S. EPA's Office of Pollution Prevention and Toxics. Washington, DC. 2005. Available from URL: http://www.epa.gov/srs/.
- ERG: Emergency Response Guidebook. A Guidebook for First Responders During the Initial Phase of a Dangerous Goods/Hazardous Materials Incident, U.S. Department of Transportation, Research and Special Programs Administration, Washington, DC, 2004.
- HSDB : Hazardous Substances Data Bank. National Library of Medicine. Bethesda, MD (Internet Version). Edition expires 1991; provided by Truven Health Analytics Inc., Greenwood Village, CO.
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