SODIUM CHROMATE ANHYDROUS
HAZARDTEXT ®
Information to help in the initial response for evaluating chemical incidents
-IDENTIFICATION
SYNONYMS
CHROMIC ACID, DISODIUM SALT CHROMIC ACID (H2CrO4), DISODIUM SALT CHROMATE OF SODA CHROMIUM DISODIUM OXIDE CHROMIUM SODIUM OXIDE DISODIUM CHROMATE NATRIUMCHROMAT (German) NEUTRAL SODIUM CHROMATE SODIUM CHROMATE SODIUM CHROMATE ANHYDROUS SODIUM CHROMATE(VI)
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.
4963372 - Sodium chromate, solution 4963369 - Sodium chromate, dry
SYNONYM REFERENCE
- (Ariel GlobalView, 2002;(CHRIS , 2002; HSDB , 2002; Lewis, 2000)
USES/FORMS/SOURCES
Sodium chromate is used in inks, paint pigments, dyes, leather tanning, and water/oil-resistant coatings (for textiles, plastics, fiberglass). It is also employed as a raw material for chromic acid, a wood preservative, a component of cells for chlorate manufacture, a chemical intermediate (strontium chromate), and in iron corrosion and rust inhibitors (e.g., sealed water cooling systems, oil-well drilling muds) (Budavari, 2000; HSDB , 2002; ITI, 1995; Lewis, 2001). The (51)Cr-labeled form of this compound is used as a diagnostic aid (blood volume determination, blood cell survival) (Budavari, 2000).
Sodium chromate can be found as deca-, tetra-, and anhydrous forms (ITI, 1995). ANHYDROUS TETRAHYDRATE The tetrahydrate form exists as yellow, slightly efflorescent, crystals (Ashford, 1994; Budavari, 2000; Lewis, 2001; ITI, 1995). The tetrahydrate crystals are also described as being somewhat deliquescent (Budavari, 2000; Lewis, 2001).
DECAHYDRATE The decahydrate form exists as translucent, efflorescent, yellow crystals. It loses water easily (is unstable with respect to water content) (Budavari, 2000; ITI, 1995; Lewis, 2001).
When dissolved in water, it appears yellow (OHM/TADS , 2002). Available grades are as follows: pure neutral; highest purity; technical (anhydrous of 99.5 percent purity); chemically pure (CP); reagent (HSDB , 2002; Lewis, 2001).
This compound is derived by melting chrome iron ore which has been crushed, dried and ground, in a reverberatory furnace with lime and soda, in the presence of air. Leached calcine also may be added. This melt is then dissolved in water, a small amount of sodium carbonate is added, the solution is decanted and acidified with acetic acid, then concentrated, and crystallized (HSDB , 2002; ILO , 1998; Lewis, 2001). High purity grades of sodium chromate may be produced through the reaction of sodium bichromate with sodium carbonate (HSDB , 2002).
SYNONYM EXPLANATION
- Sodium chromate is a hexavalent chromium compound. Please refer to the data on Chromium(VI) for additional information.
-CLINICAL EFFECTS
GENERAL CLINICAL EFFECTS
- Sodium chromate is poisonous by all exposure routes: skin, eye, lung, oral, intraperitoneal, intravenous, subcutaneous, and intradermal routes. The chromium atom in sodium chromate is Cr6+.
- Sodium chromate is an irritant and corrosive agent. Additionally, oral ingestion of sodium chromate may produce a strong emetic effect. Sodium chromate is toxic to the gastrointestinal tract through its corrosive effect. Large ingestions may cause renal and hepatic damage. Decreased or increased white blood cell counts are also possible. Because sodium chromate contains Cr+6, it has been classified as a human carcinogen.
- Ingestion of sodium chromate may cause severe gastrointestinal tract irritation, violent epigastric pain, nausea, vomiting, severe diarrhea, hemorrhage, circulatory collapse (hypovolemia), unconsciousness, and death. Renal toxicity may also be seen.
- Exposure to large doses of chromates results in nephrotoxicity. Albuminuria with desquamated cells, fatty degeneration or the kidneys and kidney necrosis with hyperemia have been reported.
- Dermal contact may cause irritant dermatitis. Chronic exposure may cause slow healing "chrome holes or sores" at the base of the nails and over knuckles.
- Eye exposure effects may range from conjunctivitis to corneal burns.
- Inhalation may cause acute lung injury. Upper airway problems include rhinitis, epistaxis, sinusitis and laryngitis. Chronic exposure may lead to nasal septum perforation and anosmia.
- For chromium compounds in general, acute toxicity occurs in two phases: an initial multi-system shock due primarily to gastrointestinal corrosion, and then a late occurring involvement of renal, hepatic, and hematopoietic systems.
- Occupational exposure to chromium compounds (Cr6+) causes eczematous dermatitis, penetrating ulcers on the hands and forearms, eye injury, inflammation of the larynx and liver, anorexia, nausea, and vomiting. Chronic inhalation of fumes causes painless ulceration, bleeding, and perforation of the nasal septum accompanied by foul nasal discharge.
- Cr6+ compounds such as sodium chromate are classified by ACGIH and IARC as carcinogens. Chronic exposure may increase cancer risk.
- 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.
ACUTE CLINICAL EFFECTS
- Sodium chromate is corrosive and can cause damage to the eyes and severe irritation of the skin, nose, throat, and respiratory tract (HSDB , 1997). If ingested, it can cause vomiting, stomach and kidney damage, severe gastroenteritis, circulatory collapse, and shock. When inhaled by guinea pigs, it was rapidly absorbed from the lungs (HSDB , 1997). Alterations in blood cell counts indicative of an allergic or inflammatory response can occur.
- In a fatal suicidal sodium chromate ingestion, thrombocytopenia, hepatic damage, and renal lesions in the distal tubules were seen. These renal findings were unusual, in that the proximal tubules are usually involved (Kurosaki et al, 1995).
CHRONIC CLINICAL EFFECTS
- Chronic exposure to hexavalent chromium compounds in general can cause ulceration of the nasal septum, slow-healing skin ulcers, and severe allergic reactions, including asthma (Moller, 1986).
- Chromium compounds frequently induce skin sensitization reactions (Clayton & Clayton, 1994).
-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.
GENERAL - 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. Monitor for respiratory distress for 72 hours. Obtain baseline chest x-ray and vital signs. Acute lung injury may require PEEP and short-term steroid therapy.
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). Ascorbic acid topically for skin exposure has been recommended for acute chromate poisoning. Ascorbic acid reduces Cr+6 to Cr+3, thus decreasing toxicity. The efficacy of this practice in humans is not proven. Animal studies have shown that to be effective ascorbic acid should be administrated as soon as possible after exposure. Repeated application of a 10% topical ascorbic acid solution has been recommended for dermal exposures. This therapy is of unproved benefit.
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 - Intravenous injection of ascorbic acid (1 gram per 0.135 gram of elemental chromium) has been recommended for systemic exposure. No studies are available which demonstrate a reduction in morbidity or mortality. In rat studies, ascorbic acid administration two hours post ingestion did not prevent renal toxicity and administration three hours post exposure appeared to enhance renal damage. One hypothesis for these outcomes is that by this time Cr+6 is already absorbed. Another concern is that ascorbic acid is metabolized to oxalate. High doses of ascorbic acid may be renal toxic, especially if renal toxicity is already present. Do not induce vomiting. Activated charcoal has not been evaluated in chromate poisoning. DILUTION: If no respiratory compromise is present, administer milk or water as soon as possible after ingestion. Dilution may only be helpful if performed in the first seconds to minutes after ingestion. The ideal amount is unknown; no more than 8 ounces (240 mL) in adults and 4 ounces (120 mL) in children is recommended to minimize the risk of vomiting. HYPOTENSION: Infuse 10 to 20 mL/kg isotonic fluid. If hypotension persists, administer dopamine (5 to 20 mcg/kg/min) or norepinephrine (ADULT: begin infusion at 0.5 to 1 mcg/min; CHILD: begin infusion at 0.1 mcg/kg/min); titrate to desired response. Monitor volume status, hematocrit, and platelet count.
-RANGE OF TOXICITY
MINIMUM LETHAL EXPOSURE
The minimum lethal human dose to this agent has not been delineated. LD50 (ORAL) = 50 to 500 mg/kg (CHRIS , 2002). Please refer to data on CHROMIUM(VI) compounds for additional information on exposure to this and other hexavalent chromium compounds.
MAXIMUM TOLERATED EXPOSURE
The maximum tolerated human exposure to this agent has not been delineated. Please refer to data on CHROMIUM(VI) compounds for additional information on exposure to this and other hexavalent chromium compounds.
One hundred ppm of chromium (administered as sodium chromate) had no observable effect on growing chicks (HSDB , 2002). Sodium chromate crystals applied topically to the intact cornea of rabbits caused localized endothelial injury and blue stromal edema; no gross buldging of the cornea occurred (Grant & Schuman, 1993). No effects on motor activity were noted in rats fed 0.07 g/L of sodium chromate in their drinking water (HSDB , 2002).
- Carcinogenicity Ratings for CAS7775-11-3 :
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): 1 ; Listed as: Sodium chromate 1 : The agent (mixture) is carcinogenic to humans. The exposure circumstance entails exposures that are carcinogenic to humans. This category is used when there is sufficient evidence of carcinogenicity in humans. Exceptionally, an agent (mixture) may be placed in this category when evidence of carcinogenicity in humans is less than sufficient but there is sufficient evidence of carcinogenicity in experimental animals and strong evidence in exposed humans that the agent (mixture) acts through a relevant mechanism of carcinogenicity.
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 CAS7775-11-3 (U.S. Environmental Protection Agency, 2011):
References: HSDB, 2002 ITI, 1995 Lewis, 2000 NTP, 2001; RTECS, 2002 LC50- (INHALATION)RAT: LD50- (INTRAVENOUS)CAT: LD50- (INTRAPERITONEAL)MOUSE: LD50- (SKIN)RABBIT: LD50- (SUBCUTANEOUS)RABBIT: LD50- (INTRAPERITONEAL)RAT: LD50- (ORAL)RAT: F344 strain, 51.91 mg/kg (HSDB, 2002) 136 mg/kg -- somnolence, general depressed activity; cardiac changes; hair affected
LDLo- (INTRAVENOUS)DOG: LDLo- (INTRADERMAL)GUINEA_PIG: LDLo- (INTRAPERITONEAL)GUINEA_PIG: LDLo- (SKIN)GUINEA_PIG: LDLo- (SUBCUTANEOUS)GUINEA_PIG: LDLo- (INTRADERMAL)RABBIT: LDLo- (INTRAVENOUS)RABBIT: LDLo- (SUBCUTANEOUS)RABBIT: TCLo- (INHALATION)HUMAN: TD- (INTRAPERITONEAL)RAT: 10 mg/kg for 24H -- administered as aqueous solution; lysozymuria; proteinuria (HSDB, 2002) 20 mg/kg for 6H -- administered as aqueous solution; lysozymuria; proteinuria (HSDB, 2002) 2 mg/kg -- significant decrease in motor activity after 1D (HSDB, 2002)
TD- (INTRAVENOUS)RAT: 0.56 mg/kg for 4D -- perivascular edema; focal necrosis of the proximal rubuli (HSDB, 2002) 2 mg/kg at 3x/W for 60 days -- liver damage (HSDB, 2002)
TD- (ORAL)RAT: TDLo- (SUBCUTANEOUS)RABBIT: TDLo- (INTRAPERITONEAL)RAT: Male, 5 mg/kg at 5D prior to mating -- affected spermatogenesis, testes, epididymis, and sperm duct
-STANDARDS AND LABELS
WORKPLACE STANDARDS
- ACGIH TLV Values for CAS7775-11-3 (American Conference of Governmental Industrial Hygienists, 2010):
- AIHA WEEL Values for CAS7775-11-3 (AIHA, 2006):
- NIOSH REL and IDLH Values for CAS7775-11-3 (National Institute for Occupational Safety and Health, 2007):
- OSHA PEL Values for CAS7775-11-3 (U.S. Occupational Safety, and Health Administration (OSHA), 2010):
- OSHA List of Highly Hazardous Chemicals, Toxics, and Reactives for CAS7775-11-3 (U.S. Occupational Safety and Health Administration, 2010):
ENVIRONMENTAL STANDARDS
- EPA CERCLA, Hazardous Substances and Reportable Quantities for CAS7775-11-3 (U.S. Environmental Protection Agency, 2010):
- EPA CERCLA, Hazardous Substances and Reportable Quantities, Radionuclides for CAS7775-11-3 (U.S. Environmental Protection Agency, 2010):
- EPA RCRA Hazardous Waste Number for CAS7775-11-3 (U.S. Environmental Protection Agency, 2010b):
- EPA SARA Title III, Extremely Hazardous Substance List for CAS7775-11-3 (U.S. Environmental Protection Agency, 2010):
- EPA SARA Title III, Community Right-to-Know for CAS7775-11-3 (40 CFR 372.65, 2006; 40 CFR 372.28, 2006):
- DOT List of Marine Pollutants for CAS7775-11-3 (49 CFR 172.101 - App. B, 2005):
- EPA TSCA Inventory for CAS7775-11-3 (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 CAS7775-11-3 (NFPA, 2002):
-HANDLING AND STORAGE
SUMMARY
Persons should avoid direct contact with sodium chromate solids and dusts. Adequate personal protective clothing and equipment should be worn when working with this compound; this includes an approved respirator, chemical protective gloves, safety goggles, protective apron and sleeves, and impervious footwear and clothing (AAR, 2000; (CHRIS , 2002; OHM/TADS , 2002). For additional information, please refer to data on CHROMIUM(VI).
HANDLING
- Persons should avoid direct contact with sodium chromate (OHM/TADS , 2002).
- Sodium chromate should be handled in a well-ventilated area, preferably a fume hood (NTP, 2001).
- Contact lenses should not be worn when working with sodium chromate (HSDB , 2002).
- Workers should change/replace/launder protective clothing daily, or more often if it becomes grossly contaminated. Contaminated protective clothing should be isolated to prevent further contamination (HSDB , 2002).
- Workers handling or exposed to sodium chromate should wash hands thoroughly with soap or a mild detergent and water prior to eating, smoking, or using the toilet (HSDB , 2002).
- Persons should not eat or smoke while working with this compound (HSDB , 2002).
- Suspension of dusts should be prevented (OHM/TADS , 2002).
STORAGE
Store this compound in tightly closed containers (Budavari, 2000; ITI, 1995; OHM/TADS , 2002). Typical containers include: 100 pound bags; fiber or steel drums; tank trucks; and tank cars (OHM/TADS , 2002).
- ROOM/CABINET RECOMMENDATIONS
Local exhaust ventilation is recommended for areas where point source emmissions to sodium chromate exist (HSDB , 2002). Storage temperatures should be ambient (CHRIS , 2002).
Keep away from combustible materials and avoid high temperatures (HSDB , 2002). Sodium chromate is a powerful oxidizer; contact with reducing agents, combustible or organic materials (e.g., paper, wood, sulfur, aluminum, plastics), or strong acids may result in violent reactions (HSDB , 2002; Lewis, 2000) NTP, 2001; (Pohanish & Greene, 1997). The decahydrate form of this compound is unstable with respect to water content (Budavari, 2000).
-PERSONAL PROTECTION
SUMMARY
- RECOMMENDED PROTECTIVE CLOTHING - EMERGENCY RESPONSE GUIDEBOOK, GUIDE 171 (ERG, 2004)
- Persons should avoid direct contact with sodium chromate solids and dusts. Adequate personal protective clothing and equipment should be worn when working with this compound; this includes an approved respirator, chemical protective gloves, safety goggles, protective apron and sleeves, and impervious footwear and clothing (AAR, 2000; (CHRIS , 2002; OHM/TADS , 2002).
- This compound will attack clothing fibers (OHM/TADS , 2002).
- For more information regarding personal protection when working with this and other hexavalent chromium compounds, please refer to the data on CHROMIC ACID and CHROMIUM(VI).
EYE/FACE PROTECTION
- Sodium chromate is an eye irritant; chemical safety goggles should be worn when working with or around this compound (CHRIS , 2002).
- Contact lenses should not be worn when working with sodium chromate (HSDB , 2002).
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 7775-11-3.
ENGINEERING CONTROLS
- Local exhaust ventilation is recommended for areas where point source emmissions to sodium chromate exist (HSDB , 2002).
-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.
Sodium chromate is a non-combustible substance; it does not burn or burns with difficulty. However, sodium chromate will increase the intensity of a fire and may cause a fire on contact with combustibles (AAR, 2000; (CHRIS , 2002). Toxic chromium oxide fumes may form when sodium chromate is involved in a fire (CHRIS , 2002; Lewis, 2000) NTP, 2001). Respiratory protection should be worn when fighting fires involving this compound (HSDB , 2002).
- FLAMMABILITY CLASSIFICATION
- NFPA Flammability Rating for CAS7775-11-3 (NFPA, 2002):
- INITIATING OR CONTRIBUTING PROPERTIES
- 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 CAS7775-11-3 (NFPA, 2002):
- Fires involving this compound should be extinguished using agents appropriate for the surrounding fire (AAR, 2000).
- Area should be flooded with water and exposed containers can be cooled with water (CHRIS , 2002).
When heated to decomposition, sodium chromate emits toxic fumes of sodium monoxide (CHRIS , 2002; Lewis, 2000) NTP, 2001).
EXPLOSION HAZARD
- Sodium chromate is a generally stable compound (CHRIS , 2002; OHM/TADS , 2002). However, it is a powerful oxidizer and contact with reducing agents, combustible or organic materials (e.g., paper, wood, sulfur, aluminum, plastics), or strong acids may result in violent reactions (HSDB , 2002; Lewis, 2000) NTP, 2001; (Pohanish & Greene, 1997).
- Hydrazine is decomposed explosively by chromates (HSDB , 2002).
- Please refer to the data on CHROMIUM(VI) for additional information.
DUST/VAPOR HAZARD
- Sodium chromate is hazardous by acute and chronic inhalation. It is a strong irritant of the lungs, eyes, and throat and may have carcinogenic potential (lung cancer) (CHRIS , 2002; HSDB , 2002; OHM/TADS , 2002).
When inhaled, sodium chromate dust may cause coughing or difficulty breathing. Ulceration of the mucous membranes and preferation of the nasal septum may result from continued exposure (CHRIS , 2002). Exposure to sodium chromate dust may result in the following symptoms or conditions: conjunctivitis, epistaxis, sinusitis, laryngitis, anosmia, chest pain, dyspnea, bronchitis, chromitosis, bronchogenic carcinoma of the lung (ITI, 1995).
- When heated to decomposition, sodium chromate emits toxic fumes of sodium monoxide (CHRIS , 2002; Lewis, 2000) NTP, 2001).
- Please refer to data on CHROMIUM(VI) for additonal information.
REACTIVITY HAZARD
- Sodium chromate is a powerful oxidizer; contact with reducing agents, combustible or organic materials (e.g., paper, wood, sulfur, aluminum, plastics), or strong acids may results in violent reactions (HSDB , 2002; Lewis, 2000) NTP, 2001; (Pohanish & Greene, 1997).
- On contact with combustible materials, sodium chromate may cause a fire (CHRIS , 2002).
- Hydrazine is decomposed explosively by chromates (HSDB , 2002).
- Please refer to the data on CHROMIUM(VI) for additional information.
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.
- Restrict access to contaminated areas for persons not wearing adequate personal protective gear and respiratory protection (HSDB , 2002). Keep upwind of spill area and avoid breathing dust or vapors (AAR, 2000).
- Wash away any sodium chromate that may have contacted the body with excess soap and water (AAR, 2000).
- AIHA ERPG Values for CAS7775-11-3 (AIHA, 2006):
- DOE TEEL Values for CAS7775-11-3 (U.S. Department of Energy, Office of Emergency Management, 2010):
Listed as Sodium chromate(VI) (Disodium chromate) TEEL-0 (units = mg/m3): 0.0156 TEEL-1 (units = mg/m3): 1.25 TEEL-2 (units = mg/m3): 7.5 TEEL-3 (units = mg/m3): 46.7 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 CAS7775-11-3 (National Research Council, 2010; National Research Council, 2009; National Research Council, 2008; National Research Council, 2007; NRC, 2001; NRC, 2002; NRC, 2003; NRC, 2004; NRC, 2004; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2006; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2007; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2005; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2005; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2007; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2006; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2006; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2006; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2006; 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National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2007; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2008; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2007; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2008; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2007; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2009; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2009; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2009; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2009; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2009; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2009; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2009; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2009; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2009; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2009; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2009; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2008; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2008; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2008; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2008; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2008; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2008; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2008; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2009; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2008; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2008; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2008; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2009; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2008; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2008; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2008; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2008; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2008; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2008; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2008; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2007; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2006; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2006; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2006; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2007; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2007; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2007; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2007; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2007; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2005; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2005; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2005; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2005; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2005; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2005; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2005; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2005; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2007; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2005; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2006; 62 FR 58840, 1997; 65 FR 14186, 2000; 65 FR 39264, 2000; 65 FR 77866, 2000; 66 FR 21940, 2001; 67 FR 7164, 2002; 68 FR 42710, 2003; 69 FR 54144, 2004):
- NIOSH IDLH Values for CAS7775-11-3 (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) Sodium chromate's primary hazard is its threat to the environment. If a spill occurs, immediate steps should be taken to prevent its spread, especially to water intakes (AAR, 2000; (CHRIS , 2002). Sodium chromate should be kept out of water sources and sewers. Dikes, pits, ponds, lagoons, or other holding areas may be used to contain flow (AAR, 2000). Persons should keep upwind from and avoid contact with spilled material. Solid spills should be covered with an impermeable flexible membrane liner (i.e., plastic sheet) to prevent material from dissolving in rain or fire fighting water (AAR, 2000; (CHRIS , 2002; HSDB , 2002). Sodium chromate sinks and mixes with water (CHRIS , 2002). If spilled in water, sodium bisulfite (NaHSO3) should be added, and the material adjusted to a neutral pH (7) by adding agricultural lime, crushed limestone, or sodium bicarbonate to the spill. Mechanical dredges or lifts may be used to remove pollutants and precipitates (AAR, 2000). Add ferric salt (FeCl3) and sodium bicarbonate (NaHCO3) to a sodium chromate spill in water to precipitate out ferric chromate, or employ an anion resin (OHM/TADS , 2002).
Personnel responding to a sodium chromate spill should wear adequate personal protective clothing and respiratory equipment (AAR, 2000; (CHRIS , 2002). Restrict access to contaminated areas for persons not wearing adequate personal protective gear and respiratory protection (HSDB , 2002). Ignition sources near the spill area should be shut off (CHRIS , 2002). For spills involving solid sodium chromate, wet methods of clean up should be used when possible to minimize airborne dust hazard (HSDB , 2002). Please refer to the data on CHROMIUM(VI) for additional information.
SMALL SPILL PRECAUTIONS - EMERGENCY RESPONSE GUIDEBOOK, GUIDE 171 (ERG, 2004) SMALL DRY SPILL PRECAUTIONS - EMERGENCY RESPONSE GUIDEBOOK, GUIDE 171 (ERG, 2004)
To dispose of sodium chromate, precipiate with a minimum of lead or barium salts, then reduce with sodium sulfite or bisulfite, ferrous sulfate, sulfur dioxide, iron or aluminum scrap, or brass chips, and precipitate as hydrous chromic oxide (OHM/TADS , 2002). For additional information on disposal methods for hexavalent chromium compounds, please refer to the data on CHROMIUM(VI). Waste management activities associated with material disposition are unique to individual situations. Proper waste characterization and decisions regarding waste management should be coordinated with the appropriate local, state, or federal authorities to ensure compliance with all applicable rules and regulations.
-ENVIRONMENTAL HAZARD MANAGEMENT
POLLUTION HAZARD
- Sodium chromate is dangerous to aquatic life in high concentrations and therefore may be dangerous if it enters water intakes (CHRIS , 2002).
- For additional information on environmental fate and kinetics of hexavalent chromium compounds, please refer to the data on CHROMIC ACID and CHROMIUM(VI).
ENVIRONMENTAL FATE AND KINETICS
SURFACE WATER In water, sodium chromate forms an acid solution which may be reduced and precipitate as the carbonate salt. This compound may convert to sodium dichromate (which is equally as dangerous as sodium chromate), but it is otherwise quite stable (OHM/TADS , 2002).
OTHER Half-life in human body: 616 days (OHM/TADS , 2002). Half-life in rat body (for sodium chromate labelled with (51)Cr and administered orally): 22.24 days (HSDB , 2002).
BIOACCUMULATION
Bioconcentration Factors (BCFs) (OHM/TADS , 2002): Marine Plants: 2000 Freshwater and Marine Invertebrates: 2000 Marine Fish: 400 Freshwater Fish: 200 Sodium chromate released in a spill situation is not likely to concentrate in the food chain at levels that are problematic (CHRIS , 2002).
Please refer to the data on CHROMIUM(VI) for additional information.
ENVIRONMENTAL TOXICITY
- Freshwater Toxicity (OHM/TADS , 2002):
LC - (WATER) GAMMARUS PULEX: 1.4 mg/L TCLo - (WATER) DAPHNIA MAGNA: <0.10 mg/L TCLo - (WATER) DAPHNIA MAGNA: 0.51 mg/L TLm - (WATER) BLUEGILL: 300 mg/L for 24H TC - (WATER) E COLI: 1-500 ppm
- Saltwater Toxicity (OHM/TADS , 2002):
- The toxic effects of sodium chromate on fish may be influenced by the pH of the aqueous environment, as evidenced by a study involving rainbow trout. Results indicate that, at all stages of the life cycle, sodium chromate is more toxic at pH 6.5 than at pH 7.8 (using survival as the criterium). The lowest concentrations that increased mortality were 0.2 mg/L at pH 6.8 and 2.0 mg/L at pH 7.8 (HSDB , 2002).
- Toxicity to aquatic plants: 0.05 ppm; to irrigable plants: 0.01 ppm (OHM/TADS , 2002).
-PHYSICAL/CHEMICAL PROPERTIES
MOLECULAR WEIGHT
DESCRIPTION/PHYSICAL STATE
- Sodium chromate can be found as deca-, tetra-, and anhydrous forms (ITI, 1995).
PH
- Sodium chromate is slightly alkaline in solution (Budavari, 2000).
SPECIFIC GRAVITY
- TEMPERATURE AND/OR PRESSURE NOT LISTED
2.723 (at 25 degrees C) (CHRIS , 2002) 1.483 (OHM/TADS , 2002; Lewis, 2001) 1.48 (decahydrate) (ITI, 1995)
DENSITY
- TEMPERATURE AND/OR PRESSURE NOT LISTED
FREEZING/MELTING POINT
780 degrees C (Lewis, 2000) 792 degrees C (HSDB , 2002) 19.92 degrees C (Lewis, 2001); 67.86 degrees F (decomposes) (NTP, 2001) 392 degrees C (Ashford, 1994) 20 degrees C (approximate) (Budavari, 2000) 19.9 degrees C (OHM/TADS , 2002) 20 degrees C (decahydrate) (ITI, 1995)
SOLUBILITY
Soluble in water (approximately 1 part water) (AAR, 2000; (Budavari, 2000; ITI, 1995; Lewis, 2001) NTP, 2001) 320 g/L (at 0 degrees C) forming alkaline solutions (Ashford, 1994) 137000 ppm (at 25 degrees C) (OHM/TADS , 2002) 873 g/L (at 30 degrees C) (HSDB , 2002)
Sodium chromate is fairly insoluble in ethanol and methanol (HSDB , 2002; Lewis, 2000). It is slightly soluble in alcohol (Budavari, 2000; ITI, 1995; Lewis, 2001) NTP, 2001).
OTHER/PHYSICAL
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