ARSENIC TRIOXIDE
HAZARDTEXT ®
Information to help in the initial response for evaluating chemical incidents
-IDENTIFICATION
SYNONYMS
Arsenic (III) oxide Arsenic sesquioxide Arsenicum album Arsenious acid Arsenious oxide Arsenious trioxide Arsenite Arsenolite Arsenous acid Arsenous acid anhydride Arsenous anhydride Arsenous oxide Arsenous oxide anhydride Arsodent Claudelite Claudetite Crude arsenic Diarsenic trioxide White arsenic CAS 1327-53-3
IDENTIFIERS
USES/FORMS/SOURCES
THERAPEUTIC USE Arsenic trioxide is used for induction of remission and consolidation in patients with acute promyelocytic leukemia (APL) with the presence of the t (15;17) translocation or PML/RAR-alpha gene expression, who are refractory to, or have relapsed from, retinoid and anthracycline chemotherapy (Prod Info TRISENOX(R) IV injection, 2010).
OTHER USES Arsenic trioxide is the most important commercial arsenic compound (Clayton & Clayton, 1994). It is the primary material used to produce all arsenical compounds, and is used as an intermediate for insecticides, herbicides, and fungicides, as a wood preservative, as a decoloring and refining agent in the manufacture of glass, in pharmaceutical preparations, pigments, and in sheep and cattle dip for preserving hides, as a textile mordant, and to purify synthetic gases (EPA, 1985; Lewis, 1993; Budavari, 1996; Morgan, 1989). About 85% of the pesticidal use of arsenic trioxide has been in liquid preparations intended to kill mice and rats (EPA, 1988). The remaining 15% has been used to kill moles, pocket gophers, and ants (EPA, 1988). However, many arsenic-containing pesticides have been banned in the US (Clayton & Clayton, 1994). For many years, arsenical pesticides were the most common cause of fatal poisoning in the US (Hayes & Laws, 1991).
THERAPEUTIC USE Arsenic trioxide injection is available as 10 mg/10 mL (1 mg/mL) sterile, clear, colorless solution in 10 mL glass, single-use ampules (Prod Info TRISENOX(R) IV injection, 2010).
OTHER USES Arsenic trioxide is obtained as a byproduct in the smelting of copper and lead concentrates (HSDB, 2006). In the United States, arsenic trioxide is mainly found in smelting of copper sulfide ores; the highest exposures are usually to roaster workers (HSDB, 2006). Arsenic trioxide in a solubilized form becomes sodium arsenite, which is more toxic than in the unsolubilized form.
-CLINICAL EFFECTS
GENERAL CLINICAL EFFECTS
- USES: Arsenic trioxide is used for induction of remission and consolidation in patients with acute promyelocytic leukemia (APL). Arsenic trioxide is the primary material used to produce all arsenical compounds, and is used as an intermediate for insecticides, herbicides, and fungicides, as a wood preservative, a decoloring and refining agent in the manufacture of glass, and a textile mordant. It is also used in pharmaceutical preparations, pigments, and in sheep and cattle dip for preserving hides.
- PHARMACOLOGY: The precise mechanism of action of arsenic trioxide in acute promyelocytic leukemia (APL) remains to be clearly defined. However, in vitro studies indicated that morphological changes and DNA fragmentation characteristic of apoptosis occur in NB4 human promyelocytic leukemia cells following arsenic trioxide administration. Selective apoptosis of APL cells mediated by activation of cysteine-proteases (caspases) may be involved. Additionally, arsenic trioxide induces damage and degradation of the fusion protein PML/RAR-alpha.
- TOXICOLOGY: Trivalent arsenic (As3+) disrupts oxidative phosphorylation, leading to free radical formation via inhibition of pyruvate dehydrogenase, which subsequently decreases gluconeogenesis due to lack of acetyl-CoA. Chronically, arsenic may cause DNA damage, mutation in the p-53 suppressor gene, and inhibition of DNA repair mechanisms leading to cancer.
- EPIDEMIOLOGY: INTRAVENOUS ROUTE: Overdose is rare. OTHER ROUTES: Toxicity from arsenic is uncommon and major effects are rare.
INTRAVENOUS ROUTE OTHER ROUTES ACUTE OVERDOSE: Arsenic compounds are mainly absorbed through the gastrointestinal tract, but some absorption may occur through intact skin or inhalation. Acute arsenic ingestion generally produces signs and symptoms within 30 minutes but symptoms may be delayed for several hours if ingested with food. Many arsenic compounds are severe irritants of the skin, eye, and mucous membranes; some may be corrosive. Contact produces local hyperemia, followed by vesicular or pustular eruptions. Trivalent compounds are particularly caustic. Acute inhalation exposures have resulted in irritation of the upper respiratory tract. MILD TO MODERATE TOXICITY: Gastrointestinal symptoms occur rapidly after acute ingestion. Initial signs and symptoms include burning lips, throat constriction, and dysphagia. Excruciating abdominal pain, severe nausea, vomiting, and profuse "rice water-like" diarrhea that may lead to hypovolemia follows these symptoms. In addition, hypovolemia from capillary leakage (third-spacing of fluids) is a common early effect. QTc prolongation may occur. Muscle cramps, facial edema, bronchitis, dyspnea, chest pain, dehydration, intense thirst, and fluid-electrolyte disturbances are also common following significant exposures. A garlic-like odor of the breath and feces may also develop. Subacute toxicity can produce neuropathies, both motor and sensory, and can progress to a Guillain-Barre like syndrome. SEVERE TOXICITY: Hypotension and tachycardia are common early signs of severe poisoning. Hypotension may be resistant to fluid resuscitation and multi-organ failure may ensue. Fever and tachypnea may occur. These patients can develop ventricular dysrhythmias including torsade de pointes. Encephalopathy, seizures and coma have been reported. Acute renal failure, hemolytic anemia, rhabdomyolysis, and hepatitis may occur several days after ingestion. CHRONIC TOXICITY: Inhalation is the most common route of exposure in arsenic workers. The sequence of chronic poisoning involves weakness, anorexia, hepatomegaly, jaundice, and gastrointestinal complaints, followed by conjunctivitis, irritation of the upper respiratory tract, hyperpigmentation, and eczematoid and allergic dermatitis. A hoarse voice and chronic upper respiratory septum is a common result after prolonged inhalation of white arsenic dust or fume. Peripheral nervous system symptoms may include numbness, burning, and tingling of the hands and feet; pain; paresthesias; tenderness; muscle fasciculations; gross tremors; ataxia; discoloration; and mental confusion. Muscular weakness, limb tenderness and difficulty walking may follow. The final phase consists of peripheral sensory neuropathy of the hands and feet. Associated motor neuropathy may occur as well. Certain arsenic compounds are known human carcinogens. Chronic exposure in either occupational settings or by drinking contaminated groundwater can cause poisoning and carries an increased risk of skin, lung, bladder, and possibly liver cancers.
INTRAVENOUS ROUTE: COMMON (greater than 20%): Nausea, vomiting, diarrhea, constipation, abdominal pain, fatigue, fever, edema, rigors, chest pain, injection site pain, sore throat, hypokalemia, hypomagnesemia, hyperglycemia, elevated liver enzymes, headache, insomnia, paresthesia, dizziness, cough, dyspnea, epistaxis, hypoxia, pleural effusion, dermatitis, pruritus, ecchymosis, tachycardia, hypotension, sinusitis, arthralgia, myalgia, bone pain, leukocytosis, anemia, anxiety. OTHER ADVERSE EFFECTS: Palmar keratosis, rashes, hyperkalemia, hypocalcemia, nausea, vomiting, diarrhea, anorexia, abdominal pain, thrombocytopenia, neutropenia, neutropenia, noncirrhotic portal hypertension, hypersensitivity reaction, tremor, peripheral neuropathy, seizure, coma, and acidosis. Patients receiving arsenic trioxide may develop QT interval prolongation, complete atrioventricular block, premature ventricular contractions (PVCs), ventricular tachycardia, and a potentially fatal torsade de pointes ventricular dysrhythmia. Retinoic acid syndrome (retinoic-acid-Acute Promyelocytic Leukemia, RA-APL, or APL differentiation syndrome), a serious adverse effect, may also occur. It is characterized by fever, skin rash, lower leg edema, weight gain, dyspnea, pulmonary infiltrates, and pleural or pericardial effusions, with or without leukocytosis and death.
- POTENTIAL HEALTH HAZARDS - EMERGENCY RESPONSE GUIDEBOOK, GUIDE 151 (ERG, 2004)
Highly toxic, may be fatal if inhaled, swallowed or absorbed through skin. Avoid any skin contact. Effects of contact or inhalation may be delayed. Fire may produce irritating, corrosive and/or toxic gases. Runoff from fire control or dilution water may be corrosive and/or toxic and cause pollution.
ACUTE CLINICAL EFFECTS
TOXICITY: Arsenic trioxide is highly poisonous. The potency of arsenic trioxide in acute exposures is a combination of several factors: whether it is dry or in solution, the purity, and the coarseness of grind of the solid form (Hayes & Laws, 1991). As much as 80% of ingested arsenic trioxide may be absorbed (Mahieu et al, 1981). TARGET ORGANS: The primary target organs initially are the gastrointestinal tract, heart, brain, and kidneys. Eventually, the skin, bone marrow, and peripheral nervous system may be significantly damaged (Finkel, 1983; Morgan, 1989; Sittig, 1985; HSDB, 2006). ONSET: Acute arsenic ingestion generally produces symptoms within 30 to 60 minutes, but symptom onset may be delayed for several hours if ingested with food (Morgan, 1989; Sittig, 1985). SIGNS AND SYMPTOMS: Hypovolemia from capillary leaking ("third spacing" of fluids) is a common early sign. The following effects have been reported: a sensation of burning, dryness, and constriction of the oral and nasal cavities, a metallic or garlic taste and garlic-like odor of the breath, vomiting, abdominal pain, dysphagia, profuse watery (rice-water-like) and sometimes bloody diarrhea, dehydration, intense thirst, fluid-electrolyte disturbances, hemolysis, pancytopenia, anemia (HSDB, 2006; Hathaway et al, 1991; Morgan, 1989; Sittig, 1985; Finkel, 1983; EPA, 1988; Kjeldsberg & Ward, 1972; Kyle & Pease, 1965). Cardiac dysrhythmias may occur, but these may be secondary to electrolyte imbalance (Peterson & Rumack, 1977; Goldsmith, 1980; St Peter et al, 1970; Sittig, 1985). Severe hypotension and metabolic acidosis were seen in a case of arsenic trioxide ingestion (Levin-Scherz et al, 1987). MEE'S LINES, transverse white lines in the nails, may be seen after acute exposure. Mee's lines commonly take 5 weeks to appear above the cuticle and advance 1 mm per week afterwards, allowing an approximation of the time of acute exposure (Heyman et al, 1956). CNS EFFECTS: ENCEPHALOPATHY: Permanent encephalopathy may ensue from acute exposure to arsenic compounds. The encephalopathy can result in atrophy of the cortex one to six months after exposure (Fincher & Koerker, 1987). This can cause loss of many higher functions. PERIPHERAL NEUROPATHY: Peripheral neuropathy of both the sensory and motor type can appear in a similar pattern regardless of the route of exposure to arsenic compounds (Finkel, 1983). It commonly begins one to 3 weeks later (Le Quesne & McLeod, 1977; Heyman et al, 1956), usually as paresthesias of the soles of the feet, then the hands, progressing proximally over the next few days (Heyman et al, 1956). Severe muscle weakness and wasting then develops (distal more so than proximal), causing disability (Donofrio et al, 1987; Le Quesne & McLeod, 1977; Heyman et al, 1956). It may initially be confused with Guillain-Barre' syndrome (Donofrio et al, 1987). Physical findings of arsenic neuropathy usually include prominently decreased sensation to touch, pinprick, and temperature, frequently in a stocking and glove distribution (Heyman et al, 1956). Loss of vibration sense is also common. Wrist drop, foot drop, and fasciculations may also occur with arsenic poisoning (Heyman et al, 1956).
CASE REPORTS: Ingestion of 9 to 14 mg was sufficient to produce signs of arsenic poisoning in a 16-month-old child (Watson et al, 1981). FATAL CASES - As little as 70 to 200 mg of arsenic trioxide ingested acutely by an adult may be lethal (Baselt & Cravey, 1989; Baselt, 1988; HSDB, 2006). Ingestion of 2 grams of arsenic trioxide in a suicide attempt was fatal despite chelation therapy, intensive supportive care, and hemodialysis (Levin-Scherz et al, 1987). Severe hypotension and metabolic acidosis were seen in a worker who died within a few hours after being buried under crude arsenic trioxide for 1 to 2 minutes at a copper smelting facility (Gerhardsson et al, 1988).
ANIMAL STUDIES: In experimental animal studies, arsenic trioxide caused edema of the eyelid and corneal injury and opacity in rabbits (Grant, 1986). TOXICOLOGY: Arsenic inhibits enzymes required for cellular respiration, and has the effect of depleting cellular energy stores, leading to cellular death (Schoolmeester & White, 1980). TREATMENT: Of six analogues of dimercaptosuccinic acid (DMSA) evaluated for efficacy in treating mice poisoned with arsenic trioxide, none were superior to DMSA for reducing either lethality or arsenic concentrations in tissues (Kreppel et al, 1993).
CHRONIC CLINICAL EFFECTS
- TOXICITY: Workers chronically exposed to arsenic by inhalation and dermal contact have developed a hoarse voice, nasal irritation, possible perforation of the nasal septum, irritation of eyes, skin, and mucous membranes, alopecia, enlarged livers, and rarely, cirrhosis of the liver (ACGIH, 1991; Finkel, 1983; Sittig, 1985; Hathaway et al, 1991; Clayton & Clayton, 1994).
- CNS: Smelter workers exposed to arsenic trioxide may also have a higher incidence of subclinical or clinical peripheral neuropathies (Feldman et al, 1979).
- ENDOCRINE: There is evidence that cumulative arsenic exposure of greater than 15 ppm-year increased the prevalence of Diabetes mellitus by an odds ratio of 10 in a population living in an area with endemically high arsenic levels in groundwater (Lai et al, 1994).
- GASTROINTESTINAL: Nausea and vomiting are infrequent complaints among arsenic workers (Clayton & Clayton, 1994).
- HEENT: Eye irritation, photophobia, dimness of vision, diplopia, and lacrimation may occur with arsenic trioxide exposure (Heyman et al, 1956; Grant, 1986).
- HEMATOLOGY: Aplastic anemia has also been described after chronic arsenic exposure (Kjeldsberg & Ward, 1972).
- HEPATIC: Noncirrhotic portal hypertension developed in a patient who had taken Fowler's solution (1 percent arsenic trioxide) for four years (Robertson & Low-Beer, 1983).
- SKIN: Skin disorders after chronic ingestion have included: melanosis, depigmentation, keratosis, and hyperkeratosis (Das D et al, 1995; Lerda, 1994).
Painful ulceration of the wrist and scrotal skin, lips, and nostrils may develop with arsenic dust exposure (Finkel, 1983; Sittig, 1985).
- OCCUPATIONAL EXPOSURE: Exposure to arsenic trioxide during glassmaking (and presumably in other occupations) can result in subacute arsenic poisoning (Ide & Bullough, 1988).
- TOLERANCE: Tolerance to arsenic can occur with repeated exposure in humans, dogs, rats, rabbits, and rats (Hayes & Laws, 1991).
-FIRST AID
FIRST AID AND PREHOSPITAL TREATMENT
- PREHOSPITAL: Remove the contaminated clothing and wash the patient thoroughly.
-MEDICAL TREATMENT
LIFE SUPPORT
- Support respiratory and cardiovascular function.
SUMMARY
- FIRST AID - EMERGENCY RESPONSE GUIDEBOOK, GUIDE 151 (ERG, 2004)
Move victim to fresh air. Call 911 or emergency medical service. Give artificial respiration if victim is not breathing. Do not use mouth-to-mouth method if victim ingested or inhaled the substance;give artificial respiration with the aid of a pocket mask equipped with a one-way valve or other proper respiratory medical device. Administer oxygen if breathing is difficult. Remove and isolate contaminated clothing and shoes. In case of contact with substance, immediately flush skin or eyes with running water for at least 20 minutes. For minor skin contact, avoid spreading material on unaffected skin. Keep victim warm and quiet. Effects of exposure (inhalation, ingestion or skin contact) to substance may be delayed. Ensure that medical personnel are aware of the material(s) involved and take precautions to protect themselves.
FIRST AID GENERAL Patients with acute arsenic poisoning usually die from hypovolemic shock secondary to vomiting and diarrhea, gastrointestinal tract bleeding, and 'third spacing' of fluids. Fluid replacement is a mainstay of initial treatment. Another threat to life is cardiac toxicity resulting in arrhythmias or cardiogenic shock. Advanced cardiac support may be required after massive acute arsenic poisoning.
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 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
-RANGE OF TOXICITY
MINIMUM LETHAL EXPOSURE
- Potentially fatal doses of arsenic trioxide have been listed as 70 to 180 mg or 1 to 2.5 mg/kg (HSDB, 2006).
- ORAL: An oral dose of 120 mg of arsenic trioxide may be fatal (Finkel, 1983). Ingestion of 2 grams of arsenic trioxide in a suicide attempt was fatal despite chelation therapy, intensive supportive care, and hemodialysis (Levin-Scherz et al, 1987).
- A worker who was buried under crude arsenic trioxide for 1 to 2 minutes died within a few hours of the exposure, despite intensive treatment (Gerhardsson et al, 1988).
- Arsenic trioxide in a solubilized form becomes sodium arsenite, which is more toxic than in an unsolubilized form. One source reported that 200 mg of arsenic trioxide ingested acutely by an adult may be lethal (Baselt & Cravey, 1989; Baselt, 1988).
MAXIMUM TOLERATED EXPOSURE
More than 50% of a group of 74 patients who took an antihistaminic herbal preparation (3.3 mg of arsenic trioxide daily) developed a sensorimotor peripheral neuropathy (HSDB , 1991). A 43-year-old man survived after ingesting 54 g of arsenic trioxide in a suicide attempt, 200 times the lethal dose (Duenas-Laita et al, 2005). A 23-year-old man intentionally ingested 1040 mg of arsenic trioxide. Clinical manifestations included severe weakness, brown watery diarrhea, vomiting, and unquenchable thirst, followed by constricted visual fields, hepatic dysfunction, dermatitis, and peripheral neuropathy. He was treated with fluid resuscitation and BAL. All of the patient's symptoms, including his visual impairment, resolved over the next 3 weeks and he was discharged without sequelae (Kamijo et al, 1998). A 33-year-old woman survived ingestion of 1850 mg of arsenic trioxide following treatment with 2,3 propanesulphonate (DMPS) and hemodialysis (Kruszewska et al, 1996). CASE SERIES: Vomiting was reported in 6 children following ingestion of all or part of an ant bait gel bar containing 0.46% arsenic trioxide (estimated total dose ranging from 5 to 45 mg). One of the children (a 20-month-old girl) also experienced several episodes of diarrhea. Initial urine arsenic concentrations ranged from 1,858 to 13,981 mcg/L. All 6 children recovered following chelation therapy with succimer (Yarris et al, 2008). A 77-year-old man developed nausea, vomiting, renal impairment, and anemia after ingesting 4 g of arsenic trioxide in a suicide attempt. With supportive care, including chelation therapy with dimercaprol (BAL), the patient gradually recovered (Yilmaz et al, 2009). A 67-year-old woman who was treated for persistent psoriasis with Fowler's solution over a 15 year period (estimated at 25 g of arsenic trioxide in all) developed noncirrhotic hepatic fibrosis as a result of the chronic arsenic poisoning (Piontek et al, 1989).
- Carcinogenicity Ratings for CAS1327-53-3 :
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: Arsenic trioxide 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): Category 1 ; Listed as: Arsenic and inorganic arsenic compounds: Arsenic trioxide 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 CAS1327-53-3 (U.S. Environmental Protection Agency, 2011):
LD50- (INTRAVENOUS)MOUSE: LD50- (ORAL)MOUSE: LD50- (SUBCUTANEOUS)MOUSE: LD50- (INTRAPERITONEAL)RAT: LD50- (ORAL)RAT: LDLo- (ORAL)CATTLE: LDLo- (SUBCUTANEOUS)CHICKEN: LDLo- (ORAL)DOG: LDLo- (ORAL)HUMAN: LDLo- (INTRAVENOUS)RABBIT: LDLo- (ORAL)RABBIT: LDLo- (SUBCUTANEOUS)RABBIT: LDLo- (SUBCUTANEOUS)RAT:
-STANDARDS AND LABELS
WORKPLACE STANDARDS
- ACGIH TLV Values for CAS1327-53-3 (American Conference of Governmental Industrial Hygienists, 2010):
- AIHA WEEL Values for CAS1327-53-3 (AIHA, 2006):
- NIOSH REL and IDLH Values for CAS1327-53-3 (National Institute for Occupational Safety and Health, 2007):
- OSHA PEL Values for CAS1327-53-3 (U.S. Occupational Safety, and Health Administration (OSHA), 2010):
- OSHA List of Highly Hazardous Chemicals, Toxics, and Reactives for CAS1327-53-3 (U.S. Occupational Safety and Health Administration, 2010):
ENVIRONMENTAL STANDARDS
- EPA CERCLA, Hazardous Substances and Reportable Quantities for CAS1327-53-3 (U.S. Environmental Protection Agency, 2010):
Listed as: Arsenic oxide As2O3 Final Reportable Quantity, in pounds (kilograms): Additional Information: Listed as: Arsenic trioxide Final Reportable Quantity, in pounds (kilograms): Additional Information:
- EPA CERCLA, Hazardous Substances and Reportable Quantities, Radionuclides for CAS1327-53-3 (U.S. Environmental Protection Agency, 2010):
- EPA RCRA Hazardous Waste Number for CAS1327-53-3 (U.S. Environmental Protection Agency, 2010b):
Listed as: Arsenic oxide As2 O3 P or U series number: P012 Footnote: Listed as: Arsenic trioxide P or U series number: P012 Footnote: Editor's Note: The D, F, and K series waste numbers and Appendix VIII to Part 261 -- Hazardous Constituents were not included. Please refer to 40 CFR Part 261.
- EPA SARA Title III, Extremely Hazardous Substance List for CAS1327-53-3 (U.S. Environmental Protection Agency, 2010):
Listed as: Arsenous Oxide Reportable Quantity, in pounds: 1 Threshold Planning Quantity, in pounds: Note(s): d
- EPA SARA Title III, Community Right-to-Know for CAS1327-53-3 (40 CFR 372.65, 2006; 40 CFR 372.28, 2006):
- DOT List of Marine Pollutants for CAS1327-53-3 (49 CFR 172.101 - App. B, 2005):
- EPA TSCA Inventory for CAS1327-53-3 (EPA, 2005):
SHIPPING REGULATIONS
- DOT -- Table of Hazardous Materials and Special Provisions for UN/NA Number 1561 (49 CFR 172.101, 2005):
- ICAO International Shipping Name for UN1561 (ICAO, 2002):
LABELS
- NFPA Hazard Ratings for CAS1327-53-3 (NFPA, 2002):
-HANDLING AND STORAGE
STORAGE
- ROOM/CABINET RECOMMENDATIONS
Store in well ventilated area away from food or food products and combustible materials (ITI, 1988). Store in a cool, dry and well-ventilated location away from acids, halogens, and iron salts (NFPA, 1991).
-PERSONAL PROTECTION
SUMMARY
- RECOMMENDED PROTECTIVE CLOTHING - EMERGENCY RESPONSE GUIDEBOOK, GUIDE 151 (ERG, 2004)
Wear positive pressure self-contained breathing apparatus (SCBA). Wear chemical protective clothing that is specifically recommended by the manufacturer. It may provide little or no thermal protection. Structural firefighters' protective clothing provides limited protection in fire situations ONLY; it is not effective in spill situations where direct contact with the substance is possible.
- Wear a self-contained positive pressure breathing apparatus when working in the vicinity of spills or leaks or when fighting fires (AAR, 1987).
- Emergency response teams should wear appropriate personal protective clothing and respiratory protection.
- Wear full protective clothing when working in the vicinity of spills or leaks or when fighting fires (AAR, 1987).
RESPIRATORY PROTECTION
- Wear a self-contained positive pressure breathing apparatus when working in the vicinity of spills or leaks or when fighting fires (AAR, 1987).
- 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 1327-53-3.
-PHYSICAL HAZARDS
FIRE HAZARD
POTENTIAL FIRE OR EXPLOSION HAZARDS - EMERGENCY RESPONSE GUIDEBOOK, GUIDE 151 (ERG, 2004) Non-combustible, substance itself does not burn but may decompose upon heating to produce corrosive and/or toxic fumes. Containers may explode when heated. Runoff may pollute waterways.
Arsenic trioxide is non-combustible, but if involved in a fire may decompose to produce toxic arsenic fumes and gaseous arsine (NFPA, 1991). Extinguish fire using agent suitable for surrounding fire (AAR, 1987). Use flooding quantities of water as a spray (AAR, 1987). Control runoff and isolate discharged material for proper disposal (NFPA, 1991).
- FLAMMABILITY CLASSIFICATION
- NFPA Flammability Rating for CAS1327-53-3 (NFPA, 2002):
- FIRE CONTROL/EXTINGUISHING AGENTS
- SMALL FIRE PRECAUTIONS - EMERGENCY RESPONSE GUIDEBOOK, GUIDE 151 (ERG, 2004)
- LARGE FIRE PRECAUTIONS - EMERGENCY RESPONSE GUIDEBOOK, GUIDE 151 (ERG, 2004)
Water spray, fog or regular foam. Move containers from fire area if you can do it without risk. Dike fire control water for later disposal; do not scatter the material. Use water spray or fog; do not use straight streams.
- TANK OR CAR/TRAILER LOAD FIRE PRECAUTIONS - EMERGENCY RESPONSE GUIDEBOOK, GUIDE 151 (ERG, 2004)
Fight fire from maximum distance or use unmanned hose holders or monitor nozzles. Do not get water inside containers. Cool containers with flooding quantities of water until well after fire is out. Withdraw immediately in case of rising sound from venting safety devices or discoloration of tank. ALWAYS stay away from tanks engulfed in fire. For massive fire, use unmanned hose holders or monitor nozzles; if this is impossible, withdraw from area and let fire burn.
- NFPA Extinguishing Methods for CAS1327-53-3 (NFPA, 2002):
- Choose an extinguishing agent suitable for fires in surrounding material (AAR, 1987).
- Water may be used in flooding quantities as fog (AAR, 1987).
When heated to decomposition, arsenic trioxide releases highly toxic fumes of oxides of arsenic and gaseous arsine (CHRIS , 1991). A mixture of arsenic trioxide with excess zinc filings will explode on heating (Bretherick, 1990). Arsenic trioxide and sodium chlorate form a spontaneously flammable mixture (NFPA, 1990). Forms toxic volatile halides in contact with halide acids. Water solution of arsenicals are in contact with active metals, e.g., arsenic, iron, aluminum, and zinc, highly toxic fumes of arsenic (including arsine) are released (HSDB , 1991).
EXPLOSION HAZARD
- When heated to decomposition, arsenic trioxide releases highly toxic fumes of oxides of arsenic and gaseous arsine (CHRIS , 1991).
- A mixture of arsenic trioxide with excess zinc filings will explode on heating (Bretherick, 1990).
- Arsenic trioxide and sodium chlorate form a spontaneously flammable mixture (NFPA, 1990).
- Forms toxic volatile halides in contact with halide acids.
- Violent reactions occur between arsenic trioxide and (ITI, 1988):
Oxygen difluoride Fluorine Chlorine trifluoride
DUST/VAPOR HAZARD
- When heated to decomposition, arsenic trioxide releases highly toxic fumes of oxides of arsenic and gaseous arsine (CHRIS , 1991).
- Forms toxic volatile halides in contact with halide acids.
- Water solution of arsenicals are in contact with active metals, e.g., arsenic, iron, aluminum, and zinc, highly toxic fumes of arsenic (including arsine) are released (HSDB , 1991).
REACTIVITY HAZARD
- When heated to decomposition, arsenic trioxide releases highly toxic fumes of oxides of arsenic and gaseous arsine (CHRIS , 1991).
- A mixture of arsenic trioxide with excess zinc filings will explode on heating (Bretherick, 1990).
- Arsenic trioxide and sodium chlorate form a spontaneously flammable mixture.
- Forms toxic volatile halides in contact with halide acids.
- Incompatibilities (Budavari, 1989):
- Violent reactions occur between arsenic trioxide and (ITI, 1988):
Oxygen difluoride Fluorine Chlorine trifluoride
- Water solution of arsenicals are in contact with active metals, e.g., arsenic, iron, aluminum, and zinc, highly toxic fumes of arsenic (including arsine) are released (HSDB , 1991).
- Corrosive to metals in the presence of moisture (AAR, 1987).
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 151 (ERG, 2004)
Increase, in the downwind direction, as necessary, the isolation distance of at least 25 to 50 meters (80 to 160 feet) in all directions.
- FIRE - PUBLIC SAFETY EVACUATION DISTANCES - EMERGENCY RESPONSE GUIDEBOOK, GUIDE 151 (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 151 (ERG, 2004)
CALL Emergency Response Telephone Number on Shipping Paper first. If Shipping Paper not available or no answer, refer to appropriate telephone number: MEXICO: SETIQ: 01-800-00-214-00 in the Mexican Republic; For calls originating in Mexico City and the Metropolitan Area: 5559-1588; For calls originating elsewhere, call: 011-52-555-559-1588.
CENACOM: 01-800-00-413-00 in the Mexican Republic; For calls originating in Mexico City and the Metropolitan Area: 5550-1496, 5550-1552, 5550-1485, or 5550-4885; For calls originating elsewhere, call: 011-52-555-550-1496, or 011-52-555-550-1552; 011-52-555-550-1485, or 011-52-555-550-4885.
ARGENTINA: CIQUIME: 0-800-222-2933 in the Republic of Argentina; For calls originating elsewhere, call: +54-11-4613-1100.
BRAZIL: PRÓ-QUÍMICA: 0-800-118270 (Toll-free in Brazil); For calls originating elsewhere, call: +55-11-232-1144 (Collect calls are accepted).
COLUMBIA: CISPROQUIM: 01-800-091-6012 in Colombia; For calls originating in Bogotá, Colombia, call: 288-6012; For calls originating elsewhere, call: 011-57-1-288-6012.
CANADA: UNITED STATES:
For additional details see the section entitled "WHO TO CALL FOR ASSISTANCE" under the ERG Instructions. As an immediate precautionary measure, isolate spill or leak area in all directions for at least 50 meters (150 feet) for liquids and at least 25 meters (75 feet) for solids. Keep unauthorized personnel away. Stay upwind. Keep out of low areas.
- When heated to decomposition, arsenic trioxide releases highly toxic fumes of oxides of arsenic and gaseous arsine (CHRIS , 1991).
- Downwind evacuation should be considered if this material is involved in a fire or if a large discharge has occurred (AAR, 1987).
- AIHA ERPG Values for CAS1327-53-3 (AIHA, 2006):
- DOE TEEL Values for CAS1327-53-3 (U.S. Department of Energy, Office of Emergency Management, 2010):
Listed as Arsenic trioxide TEEL-0 (units = mg/m3): 0.0132 TEEL-1 (units = mg/m3): 0.4 TEEL-2 (units = mg/m3): 3 TEEL-3 (units = mg/m3): 9.1 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 CAS1327-53-3 (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; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2006; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2006; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2006; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2006; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2006; United States Environmental Protection Agency Office of Pollution Prevention and Toxics, 2006; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2006; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2007; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2007; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2008; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2008; 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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):
Listed as: Arsenic trioxide Proposed Value: AEGL-1 10 min exposure: 30 min exposure: 1 hr exposure: 4 hr exposure: 8 hr exposure:
Definitions: AEGL-1 is the airborne concentration of a substance above which it is predicted that the general population, including susceptible individuals, could experience notable discomfort, irritation, or certain asymptomatic non-sensory effects. However, the effects are not disabling, are transient, and are reversible upon cessation of exposure.
Listed as: Arsenic trioxide Proposed Value: AEGL-2 10 min exposure: 30 min exposure: 1 hr exposure: 4 hr exposure: 8 hr exposure:
Definitions: AEGL-2 is the airborne concentration 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.
Listed as: Arsenic trioxide Proposed Value: AEGL-3 10 min exposure: 30 min exposure: 1 hr exposure: 4 hr exposure: 8 hr exposure:
Definitions: AEGL-3 is the airborne concentration of a substance above which it is predicted that the general population, including susceptible individuals, could experience life-threatening health effects or death.
- NIOSH IDLH Values for CAS1327-53-3 (National Institute for Occupational Safety and Health, 2007):
CONTAINMENT/WASTE TREATMENT OPTIONS
SPILL OR LEAK PRECAUTIONS - EMERGENCY RESPONSE GUIDEBOOK, GUIDE 151 (ERG, 2004) Do not touch damaged containers or spilled material unless wearing appropriate protective clothing. Stop leak if you can do it without risk. Prevent entry into waterways, sewers, basements or confined areas. Cover with plastic sheet to prevent spreading. Absorb or cover with dry earth, sand or other non-combustible material and transfer to containers. DO NOT GET WATER INSIDE CONTAINERS.
RECOMMENDED PROTECTIVE CLOTHING - EMERGENCY RESPONSE GUIDEBOOK, GUIDE 151 (ERG, 2004) Wear positive pressure self-contained breathing apparatus (SCBA). Wear chemical protective clothing that is specifically recommended by the manufacturer. It may provide little or no thermal protection. Structural firefighters' protective clothing provides limited protection in fire situations ONLY; it is not effective in spill situations where direct contact with the substance is possible.
DECONTAMINATION OF SPILLS Land Spill: Dig a pit, pond, lagoon, or holding area to contain liquid solid material. Cover solids with a plastic sheet to prevent dissolving in rain or fire fighting water (AAR, 1987).
Water Spill: Add calcium hypochlorite; then neutralize with agricultural lime, crushed limestone, or sodium bicarbonate. Add ferric chloride and adjust pH to neutral (pH=7). Use mechanical dredges or lifts to remove immobilized masses or pollutants and precipitates (AAR, 1987).
Water spray may be used to reduce or knock down vapors (AAR, 1987).
Isolate and ventilate the area. Keep sources of fire away. Wear rubber or neoprene gloves and overshoes and an approved respirator. Get fire-fighting equipment ready. Contain any liquid spill around the edge and absorb with Zorb-All(R), soil, sweeping compound, sawdust, dry sand or similar material. Dispose of absorbed or dry material in disposable containers (EPA, 1975).
-ENVIRONMENTAL HAZARD MANAGEMENT
POLLUTION HAZARD
- Arsenic trioxide occurs naturally as the mineral arsenolite (As4O6), and is formed when arsenic-containing ores are roasted. The release of gases and waste waters from ore refineries may result in the environmental release of arsenic trioxide. It may also be released to the environment from other production sites where it is further refined and used (HSDB, 2003).
- Potential for accumulation in kidney and neural tissues (OHM/TADS , 1991).
- Potential for concentration in food chain is positive; arsenic compounds tend to accumulate in oysters and the molluscan shellfish (OHM/TADS , 1991).
- SWEDEN: The background level of arsenic in Swedish lakes was 0.06 to 1.2 mcg/L (Reuther, 1992).
ENVIRONMENTAL FATE AND KINETICS
OTHER AQUATIC FATE In aerobic water, inorganic arsenic(III) is slowly oxidized to arsenic(V) at neutral pH (HSDB , 1991). Arsenic as a free element (zero-oxidation state) is rarely encountered in natural waters. Soluble inorganic arsenate (+5-oxidation state) predominates under normal conditions since it is thermodynamically more stable in water than arsenite (+3 oxidation state) (HSDB , 1991).
TERRESTRIAL FATE The half-life of arsenic trioxide in soil is 6.5 years (HSDB , 1991). The reactions of arsenicals in soil include oxidation, reduction, methylation, and demethylation. Conversion of arsenic to volatile alkylarsines leads to air transport loss from soils (HSDB , 1991). With reference to the relative amounts of annual environmental burden of arsenic, it has been calculated for 1974 that land is the major sink for arsenic, approximately 90 percent, with the atmosphere accounting for 7 to 8 percent and the smallest quantity appearing in water (HSDB , 1991). Microorganisms in sediments that contain arsenic convert arsenic in to dimethyl arsine. A variety of arsenicals are converted into dimethyl by methanobacteria (HSDB , 1991). Inorganic arsenic is more mobile than organic arsenic in soil and thus poses greater problems by leaching into surface and ground waters. Estimated half-life of arsenic in soils varies from 6.5 years for As2O3 to 16 years for Pb3(AsO4)2 (HSDB , 1991).
ATMOSPHERIC FATE With reference to the relative amounts of annual environmental burden of arsenic, it has been calculated for 1974 that land is the major sink for arsenic, approximately 90 percent, with the atmosphere accounting for 7 to 8 percent and the smallest quantity appearing in water (HSDB , 1991). Airborne particulate matter has been shown to contain both inorganic and organic arsenic compounds (HSDB , 1991).
ENVIRONMENTAL TOXICITY
- PUBLISHED VALUES (HSDB , 1991)
1. LC50 CHUM SALMON: 8,330 mcg/L/48h 2. LC50 PINK SALMON: 3,787 mcg/L/10 days 3. LC100 PINK SALMON: 7,195 mcg/L/7 days 4. LC50 FATHEAD MINNOW: 109 mg/L/96h 5. HARMFUL FISH FOOD ORGANISM: 2 to 3 mg/L 6. HARMFUL PINK SALMON: 5.3 mg/L/192h 7. HARMFUL BASS: 10 mg/L/240h 8. HARMFUL MUSSELS: 16 mg/L/72 to 384h
- BIOACCUMULATION: In a freshwater model ecosystem arsenic, as arsenate, was readily accumulated in plankton at concentrations of about 5 mcg/L. The algal population remains constant if phosphorus is added at the same concentration. Primary production was effected at As concentrations of about 50 mcg/L, although bioaccumulation did not inhabit plant growth. Phosphorus successfully competes for sediment site with arsenic and has the effect of increasing the concentration of toxic arsenic in solution (Reuther, 1992).
-PHYSICAL/CHEMICAL PROPERTIES
MOLECULAR WEIGHT
- 197.8 g (Prod Info TRISENOX(R) injection, 2005)
DESCRIPTION/PHYSICAL STATE
- ARSENIC TRIOXIDE INJECTION - A sterile, nonpyrogenic, preservative-free, clear solution of arsenic trioxide in water for injection using sodium hydroxide and dilute hydrochloride acid to adjust to pH 8 (Prod Info TRISENOX(R) injection, 2005).
- OTHER FORMS - Arsenic trioxide is odorless, tasteless, white or transparent, amorphous lumps or crystalline powder (Budavari, 1989).
- It occurs in two crystalline modifications (Budavari, 1989): Claudetite (monoclinic crystals); Arsenolite (cubic crystals).
Arsenic trioxide occurs as colorless monoclinic, cubic, or fibrous crystals, or as white or clear amorphous lumps or powder. It is odorless and tasteless. It is sparingly soluble in cold water, soluble in 15 parts boiling water, and soluble in glycerine, dilute hydrochloric acid, or alkali hydroxide. It will corrode metals under moist conditions, and is somewhat more stable at mildly acidic pH. It sublimes upon heating. Exposure to the vapors is therefore a potential hazard (HSDB, 2006; Budavari, 1996; Lewis, 1993).
VAPOR PRESSURE
- 66.1 mmHg (at 312 degrees C) (HSDB, 2006)
DENSITY
- NORMAL TEMPERATURE AND PRESSURE
- OTHER TEMPERATURE AND/OR PRESSURE
3.738 g/cm(3) (at 20 degrees C) (HSDB, 2006) Arsenolite: 3.865 g/cm(3) (at 20 degrees C) (HSDB, 2006)
FREEZING/MELTING POINT
Claudetite: 313 degrees C (Budavari, 1989) Arsenolite: 275 degrees C (Budavari, 1989)
BOILING POINT
- 465 degrees C (Budavari, 1989)
SOLUBILITY
sparingly and slowly soluble in cold water (Budavari, 1989) soluble in 15 parts boiling water (Budavari, 1989) slightly soluble in water (with hydrolysis); 20,000 ppm at 25 degrees C (OHM/TADS , 1991)
soluble in dilute hydrochloric acid solutions (Budavari, 1989) soluble in alkali hydroxide solutions (Budavari, 1989) soluble in carbonate solutions (Budavari, 1989) soluble in glycerine (Sax & Lewis, 1987)
HENRY'S CONSTANT
- 1.7x10(-12) atm-m(3)/mol (Ehrenfeld et al, 1986)
-REFERENCES
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- 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.
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