DIMETHYL SULFOXIDE (DMSO)
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
- (HSDB , 1994; OHM/TADS , 1994; RTECS , 1994)
USES/FORMS/SOURCES
MEDICAL USES Dimethyl sulfoxide (DMSO) is indicated for the symptomatic relief of interstitial cystitis (Prod Info RIMSO-50(R) intravesical irrigant, 2012). Dimethylsulfoxide is also used for extravasation caused by amsacrine, cisplatin, dactinomycin, mitomycin, and MitoXANTRONE (Gippsland Oncology Nurses Group, 2010; Wengstrom et al, 2008). Limited availability in the US (Schulmeister, 2011).
INDUSTRIAL USES Dimethyl sulfoxide is used as a solvent for acetylene, sulfur dioxide and other gases; in organic reactions; as antifreeze or hydraulic fluid when mixed with water; as a solvent for Orlon; and as a paint and varnish remover. It dissolves some hydrocarbons more than others (Budavari, 1996). It is also used as a metal-complexing agent; as a solvent for polymerization and cyanide reactions; as an analytical reagent; for spinning polyacrylonitrile and other synthetic fibers; in industrial cleaners, pesticides, and paint stripping; and in hydraulic fluids (Lewis, 1993). Products intended for industrial use may be contaminated with trace amounts of heavy metals, especially lead.
VETERINARY USES
Dimethyl sulfoxide is available as 50% w/w aqueous solution for intravesical instillation (Prod Info RIMSO-50(R) intravesical irrigant, 2012). It is also available as 99% topical solution (Prod Info Cryoserv(TM), 2003).
Dimethyl sulfoxide is an industrial solvent. It is a very hygroscopic liquid, and is prepared by air-oxidation of dimethyl sulfide in the presence of nitrogen oxides (Budavari, 1996; S Sweetman , 2001).
-CLINICAL EFFECTS
GENERAL CLINICAL EFFECTS
DMSO has shown very few toxic symptoms in humans. The most common are nausea, skin rashes, headache, and an unusual garlic-onion-oyster smell in body and breath. DMSO is a skin, eye, and respiratory tract irritant. It may cause skin irritation and reddening if spilled on clothing and allowed to remain. DMSO readily penetrates the skin and may carry other dissolved chemicals into the body. DMSO may cause urticaria and, rarely, anaphylaxis. DMSO is an experimental teratogen and also causes other reproductive effects in experimental animals. It is also a questionable carcinogen with experimental tumorigenic data.
- POTENTIAL HEALTH HAZARDS - EMERGENCY RESPONSE GUIDEBOOK, GUIDE 128 (ERG, 2004)
Inhalation or contact with material may irritate or burn skin and eyes. Fire may produce irritating, corrosive and/or toxic gases. Vapors may cause dizziness or suffocation. Runoff from fire control or dilution water may cause pollution.
-FIRST AID
FIRST AID AND PREHOSPITAL TREATMENT
-MEDICAL TREATMENT
LIFE SUPPORT
- Support respiratory and cardiovascular function.
SUMMARY
- FIRST AID - EMERGENCY RESPONSE GUIDEBOOK, GUIDE 128 (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. Wash skin with soap and water. In case of burns, immediately cool affected skin for as long as possible with cold water. Do not remove clothing if adhering to skin. Keep victim warm and quiet. Ensure that medical personnel are aware of the material(s) involved and take precautions to protect themselves.
INHALATION EXPOSURE - INHALATION: Move patient to fresh air. Monitor for respiratory distress. If cough or difficulty breathing develops, evaluate for respiratory tract irritation, bronchitis, or pneumonitis. Administer oxygen and assist ventilation as required. Treat bronchospasm with an inhaled beta2-adrenergic agonist. Consider systemic corticosteroids in patients with significant bronchospasm. If bronchospasm and wheezing occur, consider treatment with inhaled sympathomimetic agents.
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). Treat dermal irritation or burns with standard topical therapy. Patients developing dermal hypersensitivity reactions may require treatment with systemic or topical corticosteroids or antihistamines.
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 - Emesis should NOT be induced, since this is a solvent and aspiration is possible. PREHOSPITAL ACTIVATED CHARCOAL ADMINISTRATION Consider prehospital administration of activated charcoal as an aqueous slurry in patients with a potentially toxic ingestion who are awake and able to protect their airway. Activated charcoal is most effective when administered within one hour of ingestion. Administration in the prehospital setting has the potential to significantly decrease the time from toxin ingestion to activated charcoal administration, although it has not been shown to affect outcome (Alaspaa et al, 2005; Thakore & Murphy, 2002; Spiller & Rogers, 2002). In patients who are at risk for the abrupt onset of seizures or mental status depression, activated charcoal should not be administered in the prehospital setting, due to the risk of aspiration in the event of spontaneous emesis. The addition of flavoring agents (cola drinks, chocolate milk, cherry syrup) to activated charcoal improves the palatability for children and may facilitate successful administration (Guenther Skokan et al, 2001; Dagnone et al, 2002).
ACTIVATED CHARCOAL: Administer charcoal as a slurry (240 mL water/30 g charcoal). Usual dose: 25 to 100 g in adults/adolescents, 25 to 50 g in children (1 to 12 years), and 1 g/kg in infants less than 1 year old.
-RANGE OF TOXICITY
MINIMUM LETHAL EXPOSURE
MAXIMUM TOLERATED EXPOSURE
The lowest published toxic dose for man (intravenous route) was 606 mg/kg. Toxic effects were to the gastrointestinal system (nausea or vomiting) and the liver (jaundice, other not specified) (RTECS , 2001). The lowest published toxic dose for woman (dermal route) was 1800 mg/kg. Toxic effects were to the respiratory system (dyspnea, cyanosis) and hematologic (changes not specified) (RTECS , 2001).
Dimethyl sulfoxide applied intragastrically for 10 minutes in rats caused extensive mucosal damage. In concentrations of 5%, 10%, or 100%, dimethyl sulfoxide caused superficial damage to 33%, 36%, and 97%, respectively, of the corpus mucosa, and 28%, 44%, and 96%, respectively, of the antral mucosa. Concentrated dimethyl sulfoxide also caused damage to the pits and glands in some areas of the mucosa (Sorbye et al, 1993).
- Carcinogenicity Ratings for CAS67-68-5 :
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 CAS67-68-5 (U.S. Environmental Protection Agency, 2011):
LD50- (INTRAPERITONEAL)MOUSE: LD50- (INTRAVENOUS)MOUSE: LD50- (ORAL)MOUSE: LD50- (SKIN)MOUSE: LD50- (SUBCUTANEOUS)MOUSE: LD50- (INTRAPERITONEAL)RAT: LD50- (INTRAVENOUS)RAT: LD50- (ORAL)RAT: LD50- (SKIN)RAT: LD50- (SUBCUTANEOUS)RAT:
-STANDARDS AND LABELS
WORKPLACE STANDARDS
- ACGIH TLV Values for CAS67-68-5 (American Conference of Governmental Industrial Hygienists, 2010):
- AIHA WEEL Values for CAS67-68-5 (AIHA, 2006):
- NIOSH REL and IDLH Values for CAS67-68-5 (National Institute for Occupational Safety and Health, 2007):
- OSHA PEL Values for CAS67-68-5 (U.S. Occupational Safety, and Health Administration (OSHA), 2010):
- OSHA List of Highly Hazardous Chemicals, Toxics, and Reactives for CAS67-68-5 (U.S. Occupational Safety and Health Administration, 2010):
ENVIRONMENTAL STANDARDS
- EPA CERCLA, Hazardous Substances and Reportable Quantities for CAS67-68-5 (U.S. Environmental Protection Agency, 2010):
- EPA CERCLA, Hazardous Substances and Reportable Quantities, Radionuclides for CAS67-68-5 (U.S. Environmental Protection Agency, 2010):
- EPA RCRA Hazardous Waste Number for CAS67-68-5 (U.S. Environmental Protection Agency, 2010b):
- EPA SARA Title III, Extremely Hazardous Substance List for CAS67-68-5 (U.S. Environmental Protection Agency, 2010):
- EPA SARA Title III, Community Right-to-Know for CAS67-68-5 (40 CFR 372.65, 2006; 40 CFR 372.28, 2006):
- DOT List of Marine Pollutants for CAS67-68-5 (49 CFR 172.101 - App. B, 2005):
- EPA TSCA Inventory for CAS67-68-5 (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 CAS67-68-5 (NFPA, 2002):
-HANDLING AND STORAGE
-PERSONAL PROTECTION
SUMMARY
- RECOMMENDED PROTECTIVE CLOTHING - EMERGENCY RESPONSE GUIDEBOOK, GUIDE 128 (ERG, 2004)
- Butyl rubber gloves have been found to be more suitable than other types of material for resisting penetration by dimethyl sulfoxide solutions (OHM/TADS , 1994).
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 67-68-5.
-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 128 (ERG, 2004) HIGHLY FLAMMABLE: Will be easily ignited by heat, sparks or flames. Vapors may form explosive mixtures with air. Vapors may travel to source of ignition and flash back. Most vapors are heavier than air. They will spread along ground and collect in low or confined areas (sewers, basements, tanks). Vapor explosion hazard indoors, outdoors or in sewers. Those substances designated with a "P" may polymerize explosively when heated or involved in a fire. Runoff to sewer may create fire or explosion hazard. Containers may explode when heated. Many liquids are lighter than water. Substance may be transported hot. If molten aluminum is involved, refer to GUIDE 169.
Dimethyl sulfoxide is combustible when exposed to heat or flame (Lewis, 1992). It can react with oxidizing materials (Lewis, 1992).
- FLAMMABILITY CLASSIFICATION
- NFPA Flammability Rating for CAS67-68-5 (NFPA, 2002):
- FIRE CONTROL/EXTINGUISHING AGENTS
- FIRE PRECAUTIONS - EMERGENCY RESPONSE GUIDEBOOK, GUIDE 128 (ERG, 2004)
CAUTION: All these products have a very low flash point: Use of water spray when fighting fire may be inefficient. CAUTION: For mixtures containing a high percentage of an alcohol or polar solvent, alcohol-resistant foam may be more effective.
- SMALL FIRE PRECAUTIONS - EMERGENCY RESPONSE GUIDEBOOK, GUIDE 128 (ERG, 2004)
- LARGE FIRE PRECAUTIONS - EMERGENCY RESPONSE GUIDEBOOK, GUIDE 128 (ERG, 2004)
Water spray, fog or regular foam. Use water spray or fog; do not use straight streams. Move containers from fire area if you can do it without risk.
- TANK OR CAR/TRAILER LOAD FIRE PRECAUTIONS - EMERGENCY RESPONSE GUIDEBOOK, GUIDE 128 (ERG, 2004)
Fight fire from maximum distance or use unmanned hose holders or monitor nozzles. 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 CAS67-68-5 (NFPA, 2002):
- To fight fire, use foam, alcohol foam, carbon dioxide, or dry chemical (Lewis, 1992). Water may also be used (CHRIS , 1994).
When heated to decomposition, dimethyl sulfoxide emits toxic fumes of oxides of sulfur (Lewis, 1992). Formaldehyde and methyl mercaptan may also be formed (CHRIS , 1994).
EXPLOSION HAZARD
- Dimethyl sulfoxide forms a violent or explosive reaction with many acyl, aryl, and non-metal halides (listed below) (Lewis, 1992):
Acetyl chloride Benzenesulfonyl chloride Bromobenzoyl acetanilide Cyanuric chloride Disulfur dichloride Iodine pentafluoride Mg(ClO4)2 CH3Br NIO4 Oxalyl chloride P2O3 Phosphorous trichloride Phosphoryl chloride Silver fluoride Silver difluoride Sodium hydride Sulfur dichloride Sulfuryl chloride Tetrachlorosilane Thionyl chloride
- Dimethyl sulfoxide also forms violent or explosive reactions with the following (Lewis, 1992):
Boron compounds (eg, borane, nonahydrononaborate (2-) ion) 4(4'-Bromobenzoyl)acetanilide Carbonyl diisothiocyanate Copper + trichloroacetic acid Dinitrogen tetraoxide Hexachlorocyclotriphosphazine Metal alkoxides (eg, potassium tert-butoxide, sodium isopropoxide) Trifluoroacetic acid anhydride
- Dimethyl sulfoxide is incompatible with the following (Lewis, 1992):
Magnesium perchlorate Metal oxosalts Perchloric acid Periodic acid Sulfur trioxide
- Dimethyl sulfoxide forms powerfully explosive mixtures with metal salts of oxoacids (listed below) (Lewis, 1992):
Aluminum perchlorate Iron(III) nitrate Sodium perchlorate
DUST/VAPOR HAZARD
- Vapors cause moderate irritation such that personnel will find high concentrations unpleasant. The effect is temporary (CHRIS , 1994).
REACTIVITY HAZARD
- Dimethyl sulfoxide is combustible when exposed to heat or flame (Lewis, 1992).
- It can react with oxidizing materials (Lewis, 1992).
- When heated to decomposition, dimethyl sulfoxide emits toxic fumes of oxides of sulfur (Lewis, 1992). Formaldehyde and methyl mercaptan may also be formed (CHRIS , 1994).
- Dimethyl sulfoxide reacts with plastics (JEF Reynolds , 1991).
EVACUATION PROCEDURES
- Editor's Note: This material is not listed in the Table of Initial Isolation and Protective Action Distances.
- LARGE SPILL - PUBLIC SAFETY EVACUATION DISTANCES - EMERGENCY RESPONSE GUIDEBOOK, GUIDE 128 (ERG, 2004)
- FIRE - PUBLIC SAFETY EVACUATION DISTANCES - EMERGENCY RESPONSE GUIDEBOOK, GUIDE 128 (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 128 (ERG, 2004)
CALL Emergency Response Telephone Number on Shipping Paper first. If Shipping Paper not available or no answer, refer to appropriate telephone number: MEXICO: SETIQ: 01-800-00-214-00 in the Mexican Republic; For calls originating in Mexico City and the Metropolitan Area: 5559-1588; For calls originating elsewhere, call: 011-52-555-559-1588.
CENACOM: 01-800-00-413-00 in the Mexican Republic; For calls originating in Mexico City and the Metropolitan Area: 5550-1496, 5550-1552, 5550-1485, or 5550-4885; For calls originating elsewhere, call: 011-52-555-550-1496, or 011-52-555-550-1552; 011-52-555-550-1485, or 011-52-555-550-4885.
ARGENTINA: CIQUIME: 0-800-222-2933 in the Republic of Argentina; For calls originating elsewhere, call: +54-11-4613-1100.
BRAZIL: PRÓ-QUÍMICA: 0-800-118270 (Toll-free in Brazil); For calls originating elsewhere, call: +55-11-232-1144 (Collect calls are accepted).
COLUMBIA: CISPROQUIM: 01-800-091-6012 in Colombia; For calls originating in Bogotá, Colombia, call: 288-6012; For calls originating elsewhere, call: 011-57-1-288-6012.
CANADA: UNITED STATES:
For additional details see the section entitled "WHO TO CALL FOR ASSISTANCE" under the ERG Instructions. As an immediate precautionary measure, isolate spill or leak area for at least 50 meters (150 feet) in all directions. Keep unauthorized personnel away. Stay upwind. Keep out of low areas. Ventilate closed spaces before entering.
- AIHA ERPG Values for CAS67-68-5 (AIHA, 2006):
- DOE TEEL Values for CAS67-68-5 (U.S. Department of Energy, Office of Emergency Management, 2010):
Listed as Dimethyl sulfoxide (DMSO) TEEL-0 (units = mg/m3): 250 TEEL-1 (units = mg/m3): 750 TEEL-2 (units = mg/m3): 1,250 TEEL-3 (units = mg/m3): 2,000 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 CAS67-68-5 (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, 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 CAS67-68-5 (National Institute for Occupational Safety and Health, 2007):
CONTAINMENT/WASTE TREATMENT OPTIONS
SPILL OR LEAK PRECAUTIONS - EMERGENCY RESPONSE GUIDEBOOK, GUIDE 128 (ERG, 2004) ELIMINATE all ignition sources (no smoking, flares, sparks or flames in immediate area). All equipment used when handling the product must be grounded. Do not touch or walk through spilled material. Stop leak if you can do it without risk. Prevent entry into waterways, sewers, basements or confined areas. A vapor suppressing foam may be used to reduce vapors. Absorb or cover with dry earth, sand or other non-combustible material and transfer to containers. Use clean non-sparking tools to collect absorbed material.
RECOMMENDED PROTECTIVE CLOTHING - EMERGENCY RESPONSE GUIDEBOOK, GUIDE 128 (ERG, 2004) At the time of this review, criteria for land treatment or burial (sanitary landfill) disposal practices are subject to significant revision. Prior to implementing land disposal of waste residue (including waste sludge), consult with environmental regulatory agencies for guidance on acceptable disposal practices (HSDB , 1994).
-ENVIRONMENTAL HAZARD MANAGEMENT
POLLUTION HAZARD
- SOURCES: Dimethyl sulfoxide is naturally released in the environment primarily by the oxidation of dimethyl sulfide that is biologically produced in soil, water, and vegetation. It also may be released during its production, transport, disposal, and use as a solvent and medical analgesic (HSDB , 1994).
ENVIRONMENTAL FATE AND KINETICS
In the atmosphere, dimethyl sulfoxide will exist primarily in the vapor phase and be removed by both wet and dry deposition. It will react with photochemically-produced hydroxyl radicals with a half-life of about 7 hours. Dimethyl sulfoxide is hygroscopic and in a humid atmosphere, droplets of dimethyl sulfoxide will serve as a condensation nuclei for fog formation (HSDB , 1994).
SURFACE WATER If released in water, dimethyl sulfoxide should disproportionate to dimethyl sulfide and dimethyl sulfone. This disproportionation is catalyzed by light and there is some evidence that catalysts or photosensitizers in natural water may affect the rate. Dimethyl sulfoxide may also be reduced by reducing agents that may occur in natural waters. In water, volatilization, adsorption to sediment, and bioconcentration in fish should not be important (HSDB , 1994).
TERRESTRIAL If released on land, dimethyl sulfoxide would be expected to leach in the soil, due to its high water solubility. Some volatilization from dry soil and surfaces may be expected. It is fairly resistant to biodegradation based upon screening tests. Dimethyl sulfoxide may be reduced by some reducing agents that may occur in soil. If sprayed on land as an aerosol, dimethyl sulfoxide will be lost primarily by volatilization (HSDB , 1994).
OTHER When applied to plants, dimethyl sulfoxide is readily absorbed by the roots and foliage of most crop plants. While it is metabolized, especially in the foliage, unaltered dimethyl sulfoxide may be extracted from fruit and foliage (HSDB , 1994). AIR: The half-life of dimethyl sulfoxide in the atmosphere via reaction with photochemically-produced hydroxyl radicals is about 7 hours (HSDB , 1994).
ENVIRONMENTAL TOXICITY
- ECOTOXICITY VALUES (CHRIS , 1994):
TLM, bluegill, 33,500 ppm/48 hr, fresh water
- WATER: Dimethyl sulfoxide is dangerous to aquatic life in high concentrations. It may be dangerous if it enters water intakes. Notify local health and wildlife officials. Notify operators of nearby water intakes (HSDB , 1994).
The use of solvent carriers, such as dimethyl sulfoxide, may result in differences in the acute effect of toxic chemicals used in aquatic toxicity tests (Calleja & Persoone, 1993). Due to the difficulties encountered in dissolving lipophilic substances in aqueous media, solvents are often used in aquatic toxicity tests. Yet, in most cases the potential effect of the solvent is only assessed separately from that of the toxicant (Calleja & Persoone, 1993). In one study, water-insoluble chemicals such as diazepam, digoxin, and malathion were tested either in pure form or in combination with dimethyl sulfoxide, ethanol, methanol or acetone, for their acute toxicity to several aquatic invertebrates commonly used in ecotoxicology (Calleja & Persoone, 1993). The results indicated that the use of solvent carrier gave differences in the acute effect of the three chemicals to 6 test species: the crustaceans Artemia salina, Streptocephalus proboscideus, and Daphnia magna, the rotifers Brachionus plicatilis and Brachionus calyciflorus, and the bacterium Photobacterium phosphoreum (Calleja & Persoone, 1993).
-PHYSICAL/CHEMICAL PROPERTIES
MOLECULAR WEIGHT
DESCRIPTION/PHYSICAL STATE
- Dimethyl sulfoxide is a clear (water-white), very hygroscopic liquid, with slightly sulfurous odor (or practically no odor) (Budavari, 1996).
- Slightly bitter taste with a sweet after-taste (Budavari, 1996).
- Dimethyl sulfide is excreted through the lungs and skin, and is responsible for the characteristic odor (garlic-like) from patients (S Sweetman , 2001).
VAPOR PRESSURE
- 0.37 mmHg (at 20 degrees C) (Lewis, 1992)
- 0.42 mmHg (at 20 degrees C) (HSDB , 1994)
SPECIFIC GRAVITY
- OTHER TEMPERATURE AND/OR PRESSURE
FREEZING/MELTING POINT
BOILING POINT
- 189 degrees C (at 760 mmHg) (Budavari, 1996)
- 83 degrees C (at 17 mmHg) (Budavari, 1996)
- 56.6 degrees C (at 5.11 mmHg) (Budavari, 1996)
- 47.4 degrees C (at 2.82 mmHg) (Budavari, 1996)
- 30 degrees C (at 0.79 mmHg) (Budavari, 1996)
- 20 degrees C (at 0.37 mmHg) (Budavari, 1996)
FLASH POINT
- 95 degrees C; 203 degrees F (open cup) (Budavari, 1996)
AUTOIGNITION TEMPERATURE
- 419 degrees F (Lewis, 1992)
EXPLOSIVE LIMITS
SOLUBILITY
Dimethyl sulfoxide is soluble in water (Budavari, 1996). It is miscible with water, with the evolution of heat (S Sweetman , 2001).
Dimethyl sulfoxide is soluble in ethanol, acetone, ether, benzene, and chloroform (Budavari, 1996). Also soluble in alcohol (Lewis, 1993). It is NOT miscible with paraffin hydrocarbons (S Sweetman , 2001).
OTHER/PHYSICAL
1.4795 (at 20 degrees C/D) (HSDB , 1994) 1.4787 (at 21 degrees C/D) (HSDB , 1994)
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