SODIUM DODECYL BENZENESULFONATE
HAZARDTEXT ®
Information to help in the initial response for evaluating chemical incidents
-IDENTIFICATION
SYNONYMS
AA-9 AA-10 ABESON NAM ARYLAN SBC BENZENESULFONIC ACID, DODECYL-, SODIUM SALT BIO-SOFT D-40 BIO-SOFT D-35X C 550 CALSOFT F-90 CALSOFT L-40 CONCO AAS-35 CONCO AAS-40 CONCO AAS-50 CONCO AAS-35H CONCO AAS-40S CONCO AAS-45S CONOCO C 550 CONOCO C-50 CONOCO C-60 CONOCO SD 40 CONOCO SD C-40 DETERGENT HD-90 DETERLON DODECYLBENZENESULFONIC ACID SODIUM SALT DODECYLBENZENESULPHONATE, SODIUM SALT DODECYL BENZENE SODIUM SULFONATE DODECYLBENZENSULFONAN SODNY (Czech) p-DODECYLBENZENSULFONAN SODNY (Czech) ELFAN WA POWDER F 90 HS 85S KB KB (SURFACTANT) MARANIL MARLON 375 MARLON A MARLON A 350 MARLON A 375 MERCOL 25 MERCOL 30 MERPISAP AP 90P NACCANOL NR NACCANOL SW NACCANOL 35SL NANSA HS 80 NANSA HS 85S NANSA SL NANSA SS NEOPELEX 05 PELOPON A PILOT HD-90 PILOT SF-40 PILOT SF-40B RICHONATE 1850 RICHONATE 45B SANDET 60 SANTOMERSE 3 SANTOMERSE ME SANTOMERSE NO. 1 SANTOMERSE NO. 85 SDBS SINNOZON SIPONATE DS 10 SODIUM DODECYLBENZENESULFONATE SODIUM DODECYLBENZENESULFONATE, dry SODIUM DODECYLBENZENESULPHONATE SODIUM DODECYLPHENYLSULFONATE SODIUM LAURYLBENZENESULFONATE SOLAR 40 SOL SODOWA KWASU LAURYLOBENZENOSULFONOWEGO (Polish) STEINARYL NKS 50 STEINARYL NKS 100 STEPAN DS 60 STEPANTAN DS 40 SULFAPOL SULFAPOLU (Polish) SULFARIL PASTE SULFRAMIN 85 SULFRAMIN 40 FLAKES SULFRAMIN 40 GRANULAR SULFRAMIN 40RA SULFRAMIN 85 SULFRAMIN 90 FLAKES SULFRAMIN 1238 SLURRY SULFRAMIN 1240 SULFRAMIN 1250 SLURRY SULFURIL SULFURIL 50 p-1',1',4',4'-TETRAMETHYLOKTYLBENZENSULFONAN SODNY (Czech) TREPOLATE F 40 TREPOLATE F 95 ULTRAWET 1T ULTRAWET 60K ULTRAWET 99LS ULTRAWET K ULTRAWET KX ULTRAWET SK VISTA C 550 WITCONATE 60 B WITCONATE 1248 WITCONATE 1250 X 2073 BENZENE SULFONIC ACID, DODECYL-, SODIUM SALT BIO-SOFT BIO-SOFT D-60 BIO-SOFT D-62 CALSOFT CALSOFT L-60 CONCO AAS-65 CONCO AAS-90 CONCO C-50 CONCO C-60 CONCO SD 40 DODECYLBENZENE SODIUM SULFONATE DODECYLBENZENESULFONATE, SODIUM SALT NACCONOL 35SL NACCONOL 40F NACCONOL 90F NECCANOL SW PILOT SF-40FG PILOT SF-60 PILOT SF-96 PILOT SP-60 RICHONATE RICHONATE 60B SODIUM DODECYLBENZENE SULFONATE SODIUM DODECYLBENZENESULFONATE (BRANCHED CHAIN) SODIUM DODECYLBENZENESULPHONATE (BRANCHED CHAIN) SODIUM LAURLYBENZENESULFONATE SODIUM SALT DODECYLBENZENESULFONIC ACID SOLAR 90 SULFONATE DODECYLBENZENE SULFRAMIN SULFRAMIN 40 CRANULAR
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.
C18-H29-NaO3-S (Budavari, 1996) C18-H30-O3-S.Na (HSDB , 2000) C18-H30-S-O3.Na-C18-H29-NaO3-S (CHRIS , 2000)
SYNONYM REFERENCE
- (Budavari, 1996; HSDB , 2000; Lewis, 2000; OHM/TADS , 2000; RTECS , 2000)
USES/FORMS/SOURCES
Sodium dodecylbenzene sulfonate is used as an anionic detergent, as an emulsifier (emulsion polymerization, metalworking fluids), and as a surfactant (pesticides, textiles) (Ashford, 1994; Budavari, 1996). It has been used in cement admixture, latex, rubber, and polymer processing (Ashford, 1994; HSDB , 2000). It has also been used as a teat disinfectant in dairy cattle (ReproTox , 2000) and used in insecticidal dips for dogs (0.2-0.5 % final dilution). It has been used with sanitizers for poultry drinking water (30 mg/gal), for washing eggs (150 mg/gal), and on premises and equipment (300 mg/gal) (HSDB , 2000). It can be used as a growth regulator for lily (25% final dilution) (HSDB , 2000). It is used as an absorbant in pesticide and other agricultural chemicals, a foaming and wetting agent in pulp and paper products (HSDB , 2000). It is used in the foam separation of iron (III) hydroxide flox (HSDB , 2000).
Sodium dodecylbenzene sulfonate may have many isomers (Lewis, 1997a). It can be white to light yellow in color and in the form of flakes, granules, or powder (Lewis, 1997a). It is "non-volatile (vapor is water)" (CHRIS, 2000). It can be in commercially available forms containing 62% active matter or 81% purity depending on the manufacturer (Ashford, 1994; OHM/TADS , 2000).
Sodium dodecylbenzene sulfonate is derived from the alkylation of benzene with dodecene (to which benzene attaches itself in any secondary position) in the presence of an alumium chloride catalyst, then sulfonated with sulfuric acid or sulfur trioxide, followed by neutralization with caustic soda (such as sodium hydroxide or sodium carbonate) (Ashford, 1994; HSDB , 2000; Lewis, 1997a). Sodium dodecylbenzene sulfonate is a straight-chain alkylbenezene sulfonate. For stright-chained sodium dodecylbenzene sulfonate (LAS), the dodecene may be formed by Ziegler polymerization of ethylene or by cracking wax paraffins to alpha-olefins (HSDB , 2000).
-CLINICAL EFFECTS
GENERAL CLINICAL EFFECTS
- Sodium dodecylbenzene sulfonate is poisonous by the intravenous route and moderately toxic by ingestion. It is a skin and severe eye irritant. Ingestion of sodium dodecylbenzene sulfonate may cause vomiting and diarrhea; inhalation may cause coughing and labored breathing.
- In experimental animals, oral sodium dodecylbenzene sulfonate has caused lacrimation, somnolence, seizures, and spastic paralysis with or without sensory change.
- 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
- With an acute oral LD50 of 1.26 g/kg in rats, sodium dodecylbenzenesulfonate is not highly toxic. It was a severe skin irritant in rats and dogs, and a moderate skin irritant in rabbits (Zondlo, 1993). It is an eye irritant (Sderlund, 1993; BIBRA Working Group, 1990).
- It may be assumed to be a respiratory tract irritant with exposure to large amounts of the dust or aerosols (Sderlund, 1993; BIBRA Working Group, 1990). When ingested, it causes vomiting, nausea, diarrhea, and abdominal cramping (HSDB; (Sderlund, 1993).
CHRONIC CLINICAL EFFECTS
- Rats given this compound orally for 6 months had no ill effects (HSDB). There might be rare cases of allergic sensitization (HSDB).
- Dermal application of a 10 percent solution to abraded skin for 28 days produced no signs of systemic toxicity in rats; it was a severe skin irritant. Necrosis of the intestinal mucosa was seen in rats administered 2.5 to 5.0 mL/kg/day in the diet for 22 weeks. Kidney damage was produced by ingestion of 0.6% in the diet for 6 months (Zondlo, 1993).
- In dogs, necrosis of the intestines was produced by feeding 15 percent in the diet for 6 months (Zondlo, 1993).
- SDS was not a skin sensitizer in rabbits (Zondlo, 1993).
-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.
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 - Because of the potential for gastrointestinal tract irritation, DO NOT induce emesis. If swallowed and victim is unconscious or having convulsions, DO NOT attempt oral dilution. Get immediate medical attention. 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. SEIZURES: Administer a benzodiazepine; DIAZEPAM (ADULT: 5 to 10 mg IV initially; repeat every 5 to 20 minutes as needed. CHILD: 0.1 to 0.5 mg/kg IV over 2 to 5 minutes; up to a maximum of 10 mg/dose. May repeat dose every 5 to 10 minutes as needed) or LORAZEPAM (ADULT: 2 to 4 mg IV initially; repeat every 5 to 10 minutes as needed, if seizures persist. CHILD: 0.05 to 0.1 mg/kg IV over 2 to 5 minutes, up to a maximum of 4 mg/dose; may repeat in 5 to 15 minutes as needed, if seizures continue). Consider phenobarbital or propofol if seizures recur after diazepam 30 mg (adults) or 10 mg (children greater than 5 years). Monitor for hypotension, dysrhythmias, respiratory depression, and need for endotracheal intubation. Evaluate for hypoglycemia, electrolyte disturbances, and hypoxia.
-RANGE OF TOXICITY
MINIMUM LETHAL EXPOSURE
MAXIMUM TOLERATED EXPOSURE
- Carcinogenicity Ratings for CAS25155-30-0 :
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 CAS25155-30-0 (U.S. Environmental Protection Agency, 2011):
-STANDARDS AND LABELS
WORKPLACE STANDARDS
- ACGIH TLV Values for CAS25155-30-0 (American Conference of Governmental Industrial Hygienists, 2010):
- AIHA WEEL Values for CAS25155-30-0 (AIHA, 2006):
- NIOSH REL and IDLH Values for CAS25155-30-0 (National Institute for Occupational Safety and Health, 2007):
- OSHA PEL Values for CAS25155-30-0 (U.S. Occupational Safety, and Health Administration (OSHA), 2010):
- OSHA List of Highly Hazardous Chemicals, Toxics, and Reactives for CAS25155-30-0 (U.S. Occupational Safety and Health Administration, 2010):
ENVIRONMENTAL STANDARDS
- EPA CERCLA, Hazardous Substances and Reportable Quantities for CAS25155-30-0 (U.S. Environmental Protection Agency, 2010):
- EPA CERCLA, Hazardous Substances and Reportable Quantities, Radionuclides for CAS25155-30-0 (U.S. Environmental Protection Agency, 2010):
- EPA RCRA Hazardous Waste Number for CAS25155-30-0 (U.S. Environmental Protection Agency, 2010b):
- EPA SARA Title III, Extremely Hazardous Substance List for CAS25155-30-0 (U.S. Environmental Protection Agency, 2010):
- EPA SARA Title III, Community Right-to-Know for CAS25155-30-0 (40 CFR 372.65, 2006; 40 CFR 372.28, 2006):
- DOT List of Marine Pollutants for CAS25155-30-0 (49 CFR 172.101 - App. B, 2005):
- EPA TSCA Inventory for CAS25155-30-0 (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 CAS25155-30-0 (NFPA, 2002):
-HANDLING AND STORAGE
STORAGE
- ROOM/CABINET RECOMMENDATIONS
-PERSONAL PROTECTION
SUMMARY
- RECOMMENDED PROTECTIVE CLOTHING - EMERGENCY RESPONSE GUIDEBOOK, GUIDE 171 (ERG, 2004)
- Sodium dodecylbenzene sulfonate is a minimum contact hazard, but it can cause skin and eye irritation. If contact occurs, flush affected areas with plenty of water. Prolonged exposure may even cause skin rash (CHRIS , 2000).
- It may be assumed to be a respiratory tract irritant with exposure to large amounts of the dust or aerosols (Sderlund, 1993; BIBRA Working Group, 1990).
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 25155-30-0.
-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 dodecylbenzene sulfonate is combustible (Lewis, 1997). It will burn with difficulty, and it may take some effort to ignite (AAR, 1998).
- FLAMMABILITY CLASSIFICATION
- NFPA Flammability Rating for CAS25155-30-0 (NFPA, 2002):
- FIRE CONTROL/EXTINGUISHING AGENTS
- SMALL FIRE PRECAUTIONS - EMERGENCY RESPONSE GUIDEBOOK, GUIDE 171 (ERG, 2004)
- LARGE FIRE PRECAUTIONS - EMERGENCY RESPONSE GUIDEBOOK, GUIDE 171 (ERG, 2004)
Water spray, fog or regular foam. Move containers from fire area if you can do it without risk. Do not scatter spilled material with high pressure water streams. Dike fire-control water for later disposal.
- TANK FIRE PRECAUTIONS - EMERGENCY RESPONSE GUIDEBOOK, GUIDE 171 (ERG, 2004)
Cool containers with flooding quantities of water until well after fire is out. Withdraw immediately in case of rising sound from venting safety devices or discoloration of tank. ALWAYS stay away from tanks engulfed in fire.
- NFPA Extinguishing Methods for CAS25155-30-0 (NFPA, 2002):
- Use water to fight fire involving sodium dodecylbenzene sulfonate (CHRIS , 2000).
When heated to decomposition, sodium dodecylbenzene sulfonate emits toxic fumes of Na2O and sulfur oxides (ILO, 1998; Lewis, 2000).
DUST/VAPOR HAZARD
- When heated to decomposition, sodium dodecylbenzene sulfonate emits toxic fumes of Na2O (ILO, 1998; Lewis, 2000).
REACTIVITY HAZARD
- Sodium dodecylbenzene sulfonate reacts with acids or acid fumes to emit toxic fumes of sulfur oxides (HSDB , 2000; ILO, 1998).
- When heated to decomposition, sodium dodecylbenzene sulfonate emits toxic fumes of Na2O and sulfur oxides (ILO, 1998; Lewis, 2000).
EVACUATION PROCEDURES
- Editor's Note: This material is not listed in the Table of Initial Isolation and Protective Action Distances.
- SPILL - PUBLIC SAFETY EVACUATION DISTANCES - EMERGENCY RESPONSE GUIDEBOOK, GUIDE 171(ERG, 2004)
Increase, in the downwind direction, as necessary, the isolation distance of at least 50 meters (150 feet) for liquids and at least 25 meters (75 feet) for solids in all directions.
- FIRE - PUBLIC SAFETY EVACUATION DISTANCES - EMERGENCY RESPONSE GUIDEBOOK, GUIDE 171 (ERG, 2004)
If tank, rail car or tank truck is involved in a fire, ISOLATE for 800 meters (1/2 mile) in all directions; also, consider initial evacuation for 800 meters (1/2 mile) in all directions.
- PUBLIC SAFETY MEASURES - EMERGENCY RESPONSE GUIDEBOOK, GUIDE 171 (ERG, 2004)
CALL Emergency Response Telephone Number on Shipping Paper first. If Shipping Paper not available or no answer, refer to appropriate telephone number: MEXICO: SETIQ: 01-800-00-214-00 in the Mexican Republic; For calls originating in Mexico City and the Metropolitan Area: 5559-1588; For calls originating elsewhere, call: 011-52-555-559-1588.
CENACOM: 01-800-00-413-00 in the Mexican Republic; For calls originating in Mexico City and the Metropolitan Area: 5550-1496, 5550-1552, 5550-1485, or 5550-4885; For calls originating elsewhere, call: 011-52-555-550-1496, or 011-52-555-550-1552; 011-52-555-550-1485, or 011-52-555-550-4885.
ARGENTINA: CIQUIME: 0-800-222-2933 in the Republic of Argentina; For calls originating elsewhere, call: +54-11-4613-1100.
BRAZIL: PRÓ-QUÍMICA: 0-800-118270 (Toll-free in Brazil); For calls originating elsewhere, call: +55-11-232-1144 (Collect calls are accepted).
COLUMBIA: CISPROQUIM: 01-800-091-6012 in Colombia; For calls originating in Bogotá, Colombia, call: 288-6012; For calls originating elsewhere, call: 011-57-1-288-6012.
CANADA: UNITED STATES:
For additional details see the section entitled "WHO TO CALL FOR ASSISTANCE" under the ERG Instructions. As an immediate precautionary measure, isolate spill or leak area in all directions for at least 50 meters (150 feet) for liquids and at least 25 meters (75 feet) for solids. Keep unauthorized personnel away. Stay upwind.
- AIHA ERPG Values for CAS25155-30-0 (AIHA, 2006):
- DOE TEEL Values for CAS25155-30-0 (U.S. Department of Energy, Office of Emergency Management, 2010):
Listed as Sodium dodecylbenzenesulfonate (Dodecyl benzene sodium sulfonate) TEEL-0 (units = mg/m3): 4 TEEL-1 (units = mg/m3): 12.5 TEEL-2 (units = mg/m3): 75 TEEL-3 (units = mg/m3): 200 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 CAS25155-30-0 (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, 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 CAS25155-30-0 (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) Cover solid sodium dodecylbenzene sulfonate with a plastic sheet to prevent dissolving in rain or fire fighting water (AAR, 1998). Apply activated carbon at ten times the spilled amount if 10 ppm or greater concentration of solid sodium dodecylbenzene sulfonate has been spilled in water and dissolved (AAR, 1998). Keep solid and aqueous sodium dodecylbenzene sulfonate out of water intakes or other water sources and sewers, and dig holding areas as necessary (AAR, 1998; (CHRIS , 2000). Build dikes using soil, sand bags, foamed polyurethane, or foamed concrete to contain flow of aqueous sodium dodecylbenzene sulfonate. Use natural barriers or oil spill control booms to limit spill travel (AAR, 1998). Absorb bulk aqueous sodium dodecylbenzene sulfonate with fly ash, cement powder, or other commercial sorbents (AAR, 1998). Neutralize spilled aqueous sodium dodecylbenzene sulfonate with crushed limestone, soda ash, or lime (AAR, 1998). Generating foam (by using compress air and skimmers) or using carbon absorption can be effective in ameliorating aqueous sodium dodecylbenzene sulfonate (OHM/TADS , 2000). Apply water spray or mist to knock down vapors of spilled aqueous sodium dodecylbenzene sulfonate (AAR, 1998).
SMALL SPILL PRECAUTIONS - EMERGENCY RESPONSE GUIDEBOOK, GUIDE 171 (ERG, 2004) SMALL DRY SPILL PRECAUTIONS - EMERGENCY RESPONSE GUIDEBOOK, GUIDE 171 (ERG, 2004)
Hydrogen peroxide together with a ferrous sulfate catalyst can be used to oxidize sodium dodecylbenzene sulfonate (OHM/TADS , 2000). Sodium dodecylbenzene sulfonate can be injected into red clay or high iron oxide-hydroxide soils (OHM/TADS , 2000). 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
- It is harmful to aquatic life in very low concentrations, but it is not classified as a marine pollutant. Local wildlife officials and operators of nearby water intakes should be notified in case of water spill (CHRIS , 2000).
ENVIRONMENTAL FATE AND KINETICS
SURFACE WATER Sodium dodecylbenzene sulfonate should not undergo volatilization from water. Biodegradation is expected to occur in water although water temperature can affect such degradation processes (HSDB , 2000). "Bioconcentration, adsorption to sediment, and hydrolysis are not expected to be important in aquatic systems" (HSDB , 2000).
TERRESTRIAL Sodium dodecylbenzene sulfonate should have high mobility in soil. It will dissociate to dodecylbenzenesulfonic acid and sodium ion in the environment. Dodecylbenzenesulfonic acid is expected to be even more mobile than sodium dodecylbenzene sulfonate. Adsorption of sodium dodecylbenzene sulfonate is affected by the type of soil. The stronger its affinity to the soil, the slower the biodegradation process (HSDB , 2000). Biodegradation is expected to occur in aerobic soils (HSDB , 2000). Volatilization of sodium dodecylbenzene sulfonate is not expected from moist or dry soils (HSDB , 2000).
OTHER It has a half-life in air of about 23.7 hours (at an atmospheric concentration of 5x10(5) hydroxyl radicals per cubic centimeter) based on an estimated reaction rate constant of 16.22x10(-12) cm(3)/molecule-sec at 25 degrees C (HSDB , 2000). It has a half-life in water of about 15 days (OHM/TADS , 2000).
BIODEGRADATION
- It is biodegradable, and the degradation process is expected to be an important fate process in both aerobic soil and aquatic conditions (HSDB , 2000).
BIOACCUMULATION
ENVIRONMENTAL TOXICITY
- References: (OHM/TADS , 2000)
LCLo - FISH: 6 ppm - in 18 degrees C distilled water LCLo - FISH: 6 ppm - in 23 degrees C hard water LC50 - RAINBOW TROUT: 11 ppm for 24H - in static test environment LC50 - RAINBOW TROUT: 10.8 ppm for 96H - in static test environment LC50 - RAINBOW TROUT: 10.7 ppm for 336H - in static test environment LD100 - FISH: 8 ppm -- sewage treatment plant LD30 - GOLDFISH: 10 ppm for 48H -- aerated water LD100 - GOLDFISH: 15 ppm for 6H -- aerated water LD100 - SALMON: 5.6 ppm for 72H LD100 - TROUT: 5 ppm for 26-30H TL50 - RAINBOW TROUT, Juvenile: 2.04 ppm for 24H -- 11 - 15 degrees C TL50 - RAINBOW TROUT, Juvenile: 1.68 ppm for 96H -- 11 - 15 degrees C TLM - BLACK BULLHEAD: 22.0 ppm for 96H TLM - BLUEGILL: 4.2 ppm for 24H TLM - BLUEGILL: 3.7 ppm for 48H TLM - BLUEGILL: 17.0 ppm for 96H TLM - BLUEGILL: 17.4 ppm for 96H TLM - BLUNTNOSE MINNOW: 7.7 ppm for 96H TLM - CARP: 18.0 ppm for 96H TLM - COMMON SHINER: 17.0 ppm for 96H TLM - EMERALD SHINER: 7.4 ppm for 96H TLM - FATHEAD FRY: 3.1 ppm for 168H TLM - PUMPKIN SEED: 21.9 ppm for 96H TLM - ROSEFIN: 9.5 ppm for 96H TLM - SILVER JAW: 9.2 ppm for 96H TLM - STONEROLLER: 8.9 ppm for 96H TLM - TROUT: 3.7 ppm for 24H TLM - TROUT: 3 ppm for 288H
TLM - AMERICAN EEL: 7.5 ppm for 96H -- in 20 % salt environment TLM - MULLET: 10.1 ppm for 96H -- in 20 % salt environment TLM - MUMMICHOG: 22.5 ppm for 96H -- in 20 % salt environment TLM - SILVERSIDE: 7.0 ppm for 96H -- in 20 % salt environment TLM - WINTER FLOUNDER: 8.2 ppm for 96H -- in 20 % salt environment
- 3.5 ppm sodium dodecylbenzene sulfonate is toxic to plants (OHM/TADS , 2000).
-PHYSICAL/CHEMICAL PROPERTIES
MOLECULAR WEIGHT
DESCRIPTION/PHYSICAL STATE
- Sodium dodecylbenzene sulfonate may have many isomers (Lewis, 1997).
- It can be white to light yellow in color and in the forms of flakes, granules, or powder (Lewis, 1997).
- It is "non-volatile (vapor is water)" (CHRIS , 2000).
VAPOR PRESSURE
- 2.29x10(-15) mmHg (at 25 degrees C) (estimated) (HSDB , 2000)
DENSITY
- OTHER TEMPERATURE AND/OR PRESSURE
BOILING POINT
- Foams as water boils (100 degrees C) (dodecyl benezene sulfonic acid, sodium salt) (CHRIS , 2000)
- Decomposes (at 1 atm) (sodium alkylbenzenesulfonates) (CHRIS , 2000).
SOLUBILITY
Sodium dodecylbenzene sulfonate is soluble in water and is colorless when dissolved. It may foam when dissolved in water (ILO, 1998; OHM/TADS , 2000). 200,000 ppm (at 25 degrees C) (OHM/TADS , 2000) 8x10(5) mcg/L (at 20-25 degrees C) (HSDB , 2000) Soluble in water (ILO, 1998).
OCTANOL/WATER PARTITION COEFFICIENT
- log Kow = 0.45 (HSDB , 2000)
HENRY'S CONSTANT
- 6.27x10(-8) atm-m(3)/mole (estimated) (HSDB , 2000)
OTHER/PHYSICAL
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