United States Environmental Protection Agency Office of Water 4601 EPA 811-F-95-004n-T October 1 995 National Primary Drinking Water Regulations Styrene CHEMICAL/ PHYSICAL PROPERTIES CAS NUMBER: 100-42-5 COLOR/ FORM/ODOR: Colorless or yellowish oily liquid with aromatic, almost floral odor; available as polymer grade. M.P.: -30.63° C B.P.: 145.2° C VAPOR PRESSURE: 4.5 mm Hg at 25° C; highly volatile OCTANOL/WATER PARTITION (Kow): Log Kow = 2.95 DENSITY/SPEC. GRAV.: 0.906 at 20° C SOLUBILITY: 310 mg/L at 25° C; Slightly soluble in water SOIL SORPTION COEFFICIENT: Koc estimated at 520 to 555; low mobility in soil ODOR/TASTE THRESHOLDS: Taste thresh- old in water is 0.73 mg/L BlOCONCENTRATION FACTOR: BCF = 13.5 in fish; not expected to bioconcentrate in aquatic organisms. HENRY'S LAW COEFFICIENT: 0.00275 atm-cu m/mole at 25° C; rapid evaporation from water. TRADE NAMES/SYNONYMS: Vinyl benzene, Phenethylene, Cinnamene, Diarex HF 77, Styrolene, Styron, Styropol, DRINKING WATER STANDARDS MCLG: 0.1 mg/L MCL: 0.1 mg/L HAt(child): 1 day: 20 mg/L Longer-term: 2 mg/L diene latex, 5%; unsaturated polyester resins, 5%; mis- cellaneous uses, including other copolymers, 7%; ex- ports, 13%. Initially, styrene was used primarily in the synthetic rubber industry, but most styrene is currently consumed HEALTH EFFECTS SUMMARY Acute: EPA has found styrene to potentially cause the following health effects from acute exposures at levels above the MCL: nervous system effects such as depres- sion, loss of concentration, weakness, fatigue and nau- sea. Drinking water levels which are considered "safe" for short-term exposures: For a 22 Ib. child consuming 1 liter of water per day: a one-day exposure to 20 mg/L; upto a 7-year exposure to 2 mg/L. Chronic: Styrene has the potential to cause the following health effects from long-term exposures at levels above the MCL: liver and nerve tissue damage. Cancer: There is some evidence that styrene may have the potential to cause cancer from a lifetime expo- sure at levels above the MCL. USAGE PATTERNS Production of styrene has increased: from 8.5 billion os. in 1988 to 10.7 billion Ibs in 1993. In 1989, it was estimated that industries consumed styrene as follows: Polystyrene, 55%; acrylonitrile-butadiene-styrene (ABS), 10%; styrene-butadiene rubber (SBR), 5%; styrene-buta- Toxic RELEASE INVENTORY - RELEASES TO WATER AND LAND: 1987 Water TOTALS (in pounds) 275,888 Top Eight States* TX 160,411 WV 1,600 IN 0 Wl 0 OH 0 GA 0 LA 53,430 FL 0 Major Industries* Adhesives sealants 0 Concrete products 0 Synthetic rubber 152,215 Misc. plastic products 515 Plastics and resins 25,133 Boatbuilding, repair 220 Car parts, access. 0 Misc. Indust. organics 34,275 Travel trailers, campers 0 Custom plastic resins 720 * Water/Land totals only include facilities with 70 1993 Land 1,796,451 572,294 555,360 124,794 102,973 90,358 79,000 0 38,800 537,360 398,424 149,147 201,713 71,363 83,256 79,250 43,290 45,129 44,320 releases greater than a certain amount - usually 1 000 to 1 0,000 Ibs. October 1995 Technical Version ------- in plastics, resins, coatings, and paints. To date, all commercial uses are based on chemical reactions that polymerize or copolymerize styrene. RELEASE PATTERNS Styrene is released into the environment by emissions and effluents from its production and its use in polymer manufacture. It has been found in exhausts from spark- ignition engines, oxy-acetylene flames, cigarette smoke and gases emitted by pyrolysis of brake linings. Stack emissions from waste incineration have been found to contain styrene. Styrene is emitted in automobile ex- haust. Consumers may be exposed to potentially high levels of styrene monomer through contact with unsatur- ated polyester resin products used in fiberglass boat construction and repair, and as auto body fillers and casting plastics. These products may contain styrene at concentrations of 30 to 50%. Its presence in various food products is due to monomer leaching from polystyrene containers. From 1987 to 1993, according to EPA's Toxic Chemi- cal Release Inventory, styrene releases to land and water totalled over 2 million Ibs., of which about 85 percent was to land. These releases were primarily from adhesives and sealants industries. The largest releases occurred in Texas. The largest direct releases to water occurred in Louisiana. ENVIRONMENTAL FATE If released to the atmosphere, styrene will react rapidly with both hydroxyl radicals and ozone with a combined, calculated half-life of about 2.5 hours. If released to environmental bodies of water, styrene will volatilize relatively rapidly and may be subject to biodegradation. Five day aqueous theoretical BOD (TBOD) of 80% in acclimated sewage seed and 42% TBOD in an unacclimated seed have been observed. Styrene is not expected to hydrolyze. If released to soil it will biodegrade, with reports of 95% degradation from a landfill soil and 87% degradation from a sandy loam soil in 16 weeks. It is expected to leach with a low-to-moderate soil mobility, based upon a Koc of 520 to 555 estimated using regression-derived equations or structure estimation methods. Styrene is not expected to bioaccumulate or biocon- centrate in organisms and food chains to any measurable extent. A BCF of 13.5 was experimentally determined in a bioconcentration study using goldfish. Based upon its measured water solubility and log Kow, the BCF of styrene can be estimated to be approximately 24 and 100, respectively, from regression-derived equations. While styrene has been detected in various drinking waters, it was not detected in a groundwater supply survey of 945 finished water supplies which use ground- water sources. Styrene has been detected in various chemical, textile, latex, oil refinery and industrial waste- water effluents. Styrene has been frequently detected in the ambient air of source dominated locations and urban areas, has been detected in the air of a national forest in Alabama, and has been detected in the vicinity of oil fires. Food packaged in polystyrene containers has been found to contain small amounts of styrene. OTHER REGULATORY INFORMATION MONITORING: FOR GROUND/SURFACE WATER SOURCES: INITIAL FREQUENCY- 4 quarterly samples every 3 years REPEAT FREQUENCY- .Annually after 1 year of no detection TRIGGERS - Return to Initial Freq. if detect at > 0.0005 mg/L ANALYSIS: REFERENCE SOURCE EPA 600/4-88-039 METHOD NUMBERS 502.2; 524.2 TREATMENT: BEST AVAILABLE TECHNOLOGIES Granular Activated Charcoal and Packed Tower Aeration FOR ADDITIONAL INFORMATION: * EPA can provide further regulatory and other general information: EPA Safe Drinking Water Hotline - 800/426-4791 4 Other sources of lexicological and environmental fate data include: • Toxic Substance Control Act Information Line - 202/554-1404 • Toxics Release Inventory, National Library of Medicine - 301/496-6531 • Agency for Toxic Substances and Disease Registry - 404/639-6000 October 1995 Technical Version Page 2 ------- |