XYLIDINE
HAZARDTEXT ®
Information to help in the initial response for evaluating chemical incidents
-IDENTIFICATION
SYNONYMS
ACID LEATHER BROWN 2G ACID ORANGE 24 AMINODIMETHYLBENZENE AMINOXYLENE AR,AR-DIMETHYLBENZENAMINE AR,AR-DIMETHYLBENZENAMINE (SUM OF ALL ISOMERS) BENZENAMINE, AR,AR-DIMETHYL- 11460 BROWN DIMETHYLAMINOBENZENE DIMETHYLANILINE DIMETHYLPHENYLAMINE DMA RESORCINE BROWN J RESORCINE BROWN R XILIDENO (Spanish) XILIDINE (Italian) XYLIDIN (ALLE ISOMEREN) (German) XYLIDINE XYLIDINE (MIXED) XYLIDINE (MIXED ISOMERS) XYLIDINE ISOMERS XYLIDINEN (Dutch) XYLIDINE MIXED ortho-meta-para ISOMERS XYLIDINES, LIQUID XYLIDINES, SOLID XYLIDINES, SOLID OR SOLUTION XYLIDINES, SOLUTION
IDENTIFIERS
1711-Xylidines 1711-Xylidines, liquid 1711-Xylidines, solid 3452-Xylidines, solid
SYNONYM REFERENCE
- (Ariel GlobalView, 2002;(CHRIS, 2002; HSDB , 2002)ICSC, 2001;(Lewis, 2000; Pohanish, 2002; RTECS , 2002)
USES/FORMS/SOURCES
Xylidine is used in the manufacture of dyestuffs, pharmaceuticals, pesticides, agrochemicals, antioxidants and antiozonants, curing agents, polymers, synthetic resins, textile wetting agents, ore dressing frothing agents, wood preservatives and lacquers, and metal complexes (HSDB , 2002). It is also used as a gasoline additive (HSDB , 2002).
There are six xylidine isomers. Commercial xylidine is a pale yellow to brown liquid that is composed of a varying mixture of the isomers, predominately the 2,4-, 2,5-, and 2,6-isomeric forms. It possesses a weak, aromatic amine odor (Bingham et al, 2001; HSDB , 2002; Pohanish, 2002). Xylidine can be either a solid or a liquid, depending upon the isomers that comprise the mixture (AAR, 2000).
SYNONYM EXPLANATION
- This document contains data specific to the mixture of xylidine isomers (CAS 1300-73-8). For information on an individual isomer, please refer to the document specific to the isomer of interest (ie, 2,6-xylidine, CAS 87-62-7).
-CLINICAL EFFECTS
GENERAL CLINICAL EFFECTS
- Xylidine is toxic by ingestion, inhalation, and skin absorption. It may be irritating to the eyes, skin, and mucous membranes. Xylidine closely resembles aniline in its toxic effects, but is twice as toxic as aniline. It may not produce signs and symptoms such as cyanosis, headache, and dizziness, which characterizes aniline poisoning.
- Xylidine may cause liver and kidney damage and is a methemoglobin inducer. The extent of methemoglobin formation from xylidines appears to be species-dependent. Cats are more susceptible than humans and dogs less susceptible.
- No data on reproduction and prenatal toxicity in humans are available. There are no published reports of poisoning cases or epidemiological studies in workers. It has been suggested that a 1-hour exposure at 400 ppm xylidine is lethal to humans and that a long-term exposure at 10 ppm is toxic to humans.
- Experimental mutation data exist for xylidine. It is a suspected human carcinogen.
- Consumer exposure to xylidine is not expected to be significant, given its use primarily as a dye intermediate. Some exposure may occur through contact with residual material in endproduct dyes or pharmaceuticals or through contact with surface waters contaminated with the compound as a result of releases from manufacturing and use operations.
- POTENTIAL HEALTH HAZARDS - EMERGENCY RESPONSE GUIDEBOOK, GUIDE 153 (ERG, 2004)
TOXIC; inhalation, ingestion or skin contact with material may cause severe injury or death. Contact with molten substance may cause severe burns to skin and eyes. 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.
-MEDICAL TREATMENT
LIFE SUPPORT
- Support respiratory and cardiovascular function.
SUMMARY
- FIRST AID - EMERGENCY RESPONSE GUIDEBOOK, GUIDE 153 (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 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 Because of the potential for gastrointestinal tract irritation, DO NOT induce emesis. 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. OXYGEN - Administer oxygen to all cyanotic patients. METHEMOGLOBINEMIA: Determine the methemoglobin concentration and evaluate the patient for clinical effects of methemoglobinemia (ie, dyspnea, headache, fatigue, CNS depression, tachycardia, metabolic acidosis). Treat patients with symptomatic methemoglobinemia with methylene blue (this usually occurs at methemoglobin concentrations above 20% to 30%, but may occur at lower methemoglobin concentrations in patients with anemia, or underlying pulmonary or cardiovascular disorders). Administer oxygen while preparing for methylene blue therapy. METHYLENE BLUE: INITIAL DOSE/ADULT OR CHILD: 1 mg/kg IV over 5 to 30 minutes; a repeat dose of up to 1 mg/kg may be given 1 hour after the first dose if methemoglobin levels remain greater than 30% or if signs and symptoms persist. NOTE: Methylene blue is available as follows: 50 mg/10 mL (5 mg/mL or 0.5% solution) single-dose ampules and 10 mg/1 mL (1% solution) vials. Additional doses may sometimes be required. Improvement is usually noted shortly after administration if diagnosis is correct. Consider other diagnoses or treatment options if no improvement has been observed after several doses. If intravenous access cannot be established, methylene blue may also be given by intraosseous infusion. Methylene blue should not be given by subcutaneous or intrathecal injection. NEONATES: DOSE: 0.3 to 1 mg/kg. Concomitant use of methylene blue with serotonergic drugs, including serotonin reuptake inhibitors (SRIs), selective serotonin reuptake inhibitors (SSRIs), serotonin and norepinephrine reuptake inhibitors (SNRIs), tricyclic antidepressants (TCAs), norepinephrine-dopamine reuptake inhibitors (NDRIs), triptans, and ergot alkaloids may increase the risk of potentially fatal serotonin syndrome.
-RANGE OF TOXICITY
MINIMUM LETHAL EXPOSURE
The minimum lethal human dose to this agent has not been delineated. At the time of review, no published reports of poisoning cases or epidemiological studies in workers exist. It has been estimated that a one-hour exposure to 400 ppm xylidine is lethal to humans (ACGIH, 2001).
ACUTE TOXICITY STUDIES Xylidine applied to the intact skin of rabbits at a concentration of 3.3 g/kg for longer than one hour can result in cyanosis and death, but will not produce noticeable local effects on the skin (HSDB , 2002).
CHRONIC TOXICITY STUDIES Cats repeatedly exposed to 138 ppm xylidine developed loss of leg coordination, cyanosis, and death. Upon autopsy, pulmonary edema and lobular pneumonia, necrosis of the liver, and toxic nephrosis were observed (HSDB , 2002).
MAXIMUM TOLERATED EXPOSURE
The maximum tolerated human exposure to this agent has not been delineated. At the time of review, no published reports of poisoning cases or epidemiological studies in workers exist. It has been estimated that a long-term exposure to 10 ppm is toxic to humans (ACGIH, 2001).
ACUTE TOXICITY STUDIES Administered intravenously to cats, 0.28 mmol/kg of xylidine produced 10% methemoglobin, whereas similar exposure in dogs did not produce methemoglobin (Hathaway et al, 1996).
CHRONIC TOXICITY STUDIES Oral doses of 2 to 50 mg/kg given over the course of four weeks induced fatty liver degeneration in dogs. In rats, 20 to 700 mg/kg given orally for four weeks induced hepatomegaly (HSDB , 2002). Cats exposed to 132 ppm for three days developed methemoglobin levels of 55%. Repeated exposure to 17.4 ppm resulted in toxic hepatitis. No adverse effects were observed after repeated exposure to 7.8 ppm (HSDB , 2002).
CARCINOGENICITY ACGIH assigns xylidine a rating of A3, Confirmed Animal Carcinogen with Unknown Relevance to Humans, based on the increased occurrence of vascular tumors in mice and nasal cavity carcinomas in rats exposed to xylidine in feeding studies (ACGIH, 2001). Editor's Note: Some xylidine isomers have been categorized separately from the mixture. Please refer to the document specific to the isomer of interest for information on these ratings.
- Carcinogenicity Ratings for CAS1300-73-8 :
ACGIH (American Conference of Governmental Industrial Hygienists, 2010): A3 ; Listed as: Xylidine (mixed isomers) A3 :Confirmed Animal Carcinogen with Unknown Relevance to Humans: The agent is carcinogenic in experimental animals at a relatively high dose, by route(s) of administration, at site(s), of histologic type(s), or by mechanism(s) that may not be relevant to worker exposure. Available epidemiologic studies do not confirm an increased risk of cancer in exposed humans. Available evidence does not suggest that the agent is likely to cause cancer in humans except under uncommon or unlikely routes or levels of exposure.
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 ; Listed as: Xylidine 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 CAS1300-73-8 (U.S. Environmental Protection Agency, 2011):
-STANDARDS AND LABELS
WORKPLACE STANDARDS
- ACGIH TLV Values for CAS1300-73-8 (American Conference of Governmental Industrial Hygienists, 2010):
Editor's Note: The listed values are recommendations or guidelines developed by ACGIH(R) to assist in the control of health hazards. They should only be used, interpreted and applied by individuals trained in industrial hygiene. Before applying these values, it is imperative to read the introduction to each section in the current TLVs(R) and BEI(R) Book and become familiar with the constraints and limitations to their use. Always consult the Documentation of the TLVs(R) and BEIs(R) before applying these recommendations and guidelines.
- AIHA WEEL Values for CAS1300-73-8 (AIHA, 2006):
- NIOSH REL and IDLH Values for CAS1300-73-8 (National Institute for Occupational Safety and Health, 2007):
Listed as: Xylidine REL: IDLH: IDLH: 50 ppm Note(s): Not Listed
- OSHA PEL Values for CAS1300-73-8 (U.S. Occupational Safety, and Health Administration (OSHA), 2010):
Listed as: Xylidine Table Z-1 for Xylidine: 8-hour TWA: ppm: 5 mg/m3: 25 Ceiling Value: Skin Designation: Yes Notation(s): Not Listed
- OSHA List of Highly Hazardous Chemicals, Toxics, and Reactives for CAS1300-73-8 (U.S. Occupational Safety and Health Administration, 2010):
ENVIRONMENTAL STANDARDS
- EPA CERCLA, Hazardous Substances and Reportable Quantities for CAS1300-73-8 (U.S. Environmental Protection Agency, 2010):
- EPA CERCLA, Hazardous Substances and Reportable Quantities, Radionuclides for CAS1300-73-8 (U.S. Environmental Protection Agency, 2010):
- EPA RCRA Hazardous Waste Number for CAS1300-73-8 (U.S. Environmental Protection Agency, 2010b):
- EPA SARA Title III, Extremely Hazardous Substance List for CAS1300-73-8 (U.S. Environmental Protection Agency, 2010):
- EPA SARA Title III, Community Right-to-Know for CAS1300-73-8 (40 CFR 372.65, 2006; 40 CFR 372.28, 2006):
- DOT List of Marine Pollutants for CAS1300-73-8 (49 CFR 172.101 - App. B, 2005):
- EPA TSCA Inventory for CAS1300-73-8 (EPA, 2005):
SHIPPING REGULATIONS
- DOT -- Table of Hazardous Materials and Special Provisions for UN/NA Number 1711 (49 CFR 172.101, 2005):
- DOT -- Table of Hazardous Materials and Special Provisions for UN/NA Number 3452 (49 CFR 172.101, 2005):
- ICAO International Shipping Name for UN1711 (ICAO, 2002):
Proper Shipping Name: Xylidines, liquid UN Number: 1711 Proper Shipping Name: Xylidines, solid UN Number: 1711
- ICAO International Shipping Name for UN3452 (ICAO, 2002):
LABELS
- NFPA Hazard Ratings for CAS1300-73-8 (NFPA, 2002):
-HANDLING AND STORAGE
SUMMARY
Xylidine is toxic to humans through all routes of exposure (inhalation, ingestion, and dermal contact) (HSDB , 2002; Lewis, 2001). Adequate personal protection should be worn to prevent contact with this material. This includes a self-contained breathing apparatus, full chemical protective clothing, and splash-proof safety goggles (HSDB , 2002) ICSC, 2001; (NFPA, 2002a; NIOSH , 2002; Pohanish, 2002).
HANDLING
- Wear adequate protective clothing and splash-proof safety goggles to prevent skin or eye contact with liquid xylidine (HSDB , 2002; Pohanish, 2002).
- Eyewash fountains should be provided in areas where xylidine is stored or handled (HSDB , 2002; Pohanish, 2002).
- Contact lenses should not be worn when working with xylidine (Pohanish, 2002).
- If xylidine contacts the skin, rinse the chemical off and then wash affected areas with soap and water (ICSC, 2001; (Pohanish, 2002). If xylidine contacts the eyes, remove any contact lenses, flush the eye(s) with water for at least 15 minutes, and seek medical attention (Pohanish, 2002).
- Only non-sparking tools and equipment should be used when working around xylidine, especially when opening and closing containers (Pohanish, 2002).
- Smoking should be prohibited in areas where xylidine is handled, used, or stored (Pohanish, 2002).
STORAGE
Keep containers of liquid xylidine tightly closed (Pohanish, 2002). Liquid xylidine may attack some rubber, plastics, and coatings (HSDB , 2002). Drums used to store xylidine should be equipped with self-closing valves, pressure vacuum bungs, and flame arresters (Pohanish, 2002). Any metal containers used during the transfer of greater than five gallons of xylidine should be grounded and bonded (Pohanish, 2002). Common shipping containers for xylidine include glass bottles, metal cans, pails, and drums (NFPA, 2002a).
- ROOM/CABINET RECOMMENDATIONS
Store xylidine in a cool, dry, well-ventilated location away from sources of heat or ignition (NFPA, 2002a; Pohanish, 2002). Outside or detached storage is preferred (NFPA, 2002a). Xylidine should be stored away from strong oxidizers, hypochlorite bleaches, and heat (HSDB , 2002).
Keep separate from strong oxidizers, acids, acid anhydrides, acid chlorides, isocyanates, aldehydes, hypochlorites, chloroformates, and halogens (NFPA, 2002a; Pohanish & Greene, 1997). Xylidine can react vigorously with oxidizing materials (Lewis, 2000; NFPA, 2002a). Contact with strong acids may result in explosions (Pohanish & Greene, 1997). Contact with hypochlorite bleaches results in the production of explosive chloroamines (ILO, 1998; NFPA, 2002a; Pohanish & Greene, 1997). Xylidines are incompatible with strong acids, organic acids and anhydrides, isocyanates, and aldehydes (Pohanish & Greene, 1997). Liquid xylidine will attack some forms of plastics, rubber, and coatings (Pohanish & Greene, 1997).
-PERSONAL PROTECTION
SUMMARY
- RECOMMENDED PROTECTIVE CLOTHING - EMERGENCY RESPONSE GUIDEBOOK, GUIDE 153 (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. fire situations ONLY; it is not effective in spill situations where direct contact with the substance is possible.
- Adequate personal protection should be worn to prevent contact with xylidine. This includes a self-contained breathing apparatus, full chemical protective clothing, and splash-proof safety goggles (HSDB , 2002; (ICSC, 1998); NFPA, 2002a; NIOSH , 2002; Pohanish, 2002).
- Wear adequate protective clothing and splash-proof safety goggles to prevent skin or eye contact with liquid xylidine (HSDB , 2002; Pohanish, 2002).
- "Non-impervious clothing which becomes contaminated with xylidine should be removed immediately and not reworn until the xylidine is removed from the clothing" (HSDB , 2002).
- Segregate protective clothing that has been in contact with the compound so those who handle or clean the clothing take appropriate precautions (HSDB , 2002).
EYE/FACE PROTECTION
- Wear splash-proof safety goggles to prevent skin or eye contact with liquid xylidine (HSDB , 2002; Pohanish, 2002).
- Eyewash fountains should be provided in areas in which xylidine is stored or handled (HSDB , 2002; Pohanish, 2002).
- Contact lenses should not be worn when working with xylidine (Pohanish, 2002).
RESPIRATORY PROTECTION
- Refer to "Recommendations for respirator selection" in the NIOSH Pocket Guide to Chemical Hazards on TOMES Plus(R) for respirator information.
PROTECTIVE CLOTHING
- CHEMICAL PROTECTIVE CLOTHING. Search results for CAS 1300-73-8.
-PHYSICAL HAZARDS
FIRE HAZARD
POTENTIAL FIRE OR EXPLOSION HAZARDS - EMERGENCY RESPONSE GUIDEBOOK, GUIDE 153 (ERG, 2004) Combustible material: may burn but does not ignite readily. When heated, vapors may form explosive mixtures with air: indoors, outdoors and sewers explosion hazards. Those substances designated with a "P" may polymerize explosively when heated or involved in a fire. Contact with metals may evolve flammable hydrogen gas. Containers may explode when heated. Runoff may pollute waterways. Substance may be transported in a molten form.
Xylidine is combustible (ICSC, 2001; (NFPA, 2002a; Pohanish, 2002). Xylidine is combustible when exposed to heat or flame (Lewis, 2000). Contact with strong acids may cause fire (Pohanish & Greene, 1997).
- FLAMMABILITY CLASSIFICATION
- NFPA Flammability Rating for CAS1300-73-8 (NFPA, 2002):
- INITIATING OR CONTRIBUTING PROPERTIES
Xylidine is a combustible liquid with a flashpoint of 91 to 96 degrees C (ACGIH, 2001; ILO, 1998; Pohanish & Greene, 1997).
- FIRE CONTROL/EXTINGUISHING AGENTS
- SMALL FIRE PRECAUTIONS - EMERGENCY RESPONSE GUIDEBOOK, GUIDE 153 (ERG, 2004)
- LARGE FIRE PRECAUTIONS - EMERGENCY RESPONSE GUIDEBOOK, GUIDE 153 (ERG, 2004)
Dry chemical, CO2, alcohol-resistant foam or water spray. Move containers from fire area if you can do it without risk. Dike fire control water for later disposal; do not scatter the material.
- TANK OR CAR/TRAILER LOAD FIRE PRECAUTIONS - EMERGENCY RESPONSE GUIDEBOOK, GUIDE 153 (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.
- NFPA Extinguishing Methods for CAS1300-73-8 (NFPA, 2002):
- To fight fires involving xylidine, use dry chemical, foam, or carbon dioxide. Approach fires from upwind to avoid exposure to toxic decomposition products and hazardous vapors (HSDB , 2002; Lewis, 2000; NFPA, 2002a; Pohanish, 2002).
Water may be ineffective on fires involving xylidines, and may cause frothing (HSDB , 2002; NFPA, 2002a).
- Use water spray to cool containers of xylidine exposed to fire (Pohanish, 2002). Containers may explode violently in the heat of a fire (HSDB , 2002).
- "Extinguish fire using agent suitable for type of surrounding fire. (Material itself does not burn or burns with difficulty.) Use water in flooding quantities as fog. Cool all affected containers with flooding quantities of water. Apply water from as far a distance as possible" (AAR, 2000).
Hazardous nitrogen oxide vapors are emitted when xylidine is heated to decomposition (ILO, 1998; Lewis, 2000; NFPA, 2002a; Pohanish, 2002).
EXPLOSION HAZARD
- Xylidine vapor forms an explosive mixture with air above 96 degrees C ((ICSC, 1998); Pohanish & Greene, 1997).
- Contact with strong acids may result in explosions (Pohanish & Greene, 1997).
- Contact with hypochlorite bleaches results in the production of explosive chloroamines (ILO, 1998; Pohanish & Greene, 1997; Pohanish, 2002).
- Containers of xylidine exposed to the heat of a fire may explode violently (HSDB , 2002).
DUST/VAPOR HAZARD
- Xylidine vapors are toxic by inhalation (ILO, 1998; Lewis, 2001; Pohanish, 2002). Symptoms of exposure include eye, skin, and respiratory tract irritation, confusion, methemoglobinemia, headaches, dizziness, convulsions, nausea, vomiting, and cyanosis. At high concentrations, xylidine vapor may cause difficulty breathing, unconsciousness, liver damage, and death (ILO, 1998; Pohanish, 2002).
- Hazardous nitrogen oxide vapors are emitted when xylidine is heated to decomposition (Lewis, 2000; NFPA, 2002a; Pohanish, 2002).
- Xylidine vapors will form explosive mixtures with air at temperatures above 96 degrees C ((ICSC, 1998); Pohanish & Greene, 1997).
REACTIVITY HAZARD
- Xylidine can react vigorously with oxidizing materials (Lewis, 2000; NFPA, 2002a). Contact with strong acids may result in explosions (Pohanish & Greene, 1997).
- Contact with hypochlorite bleaches results in the production of explosive chloroamines (ILO, 1998; NFPA, 2002a; Pohanish & Greene, 1997).
- Xylidines are incompatible with strong acids, organic acids and anhydrides, isocyanates, and aldehydes (Pohanish & Greene, 1997).
- Liquid xylidine will attack some forms of plastics, rubber, and coatings (Pohanish & Greene, 1997).
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 153 (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 153 (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 153 (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. Ventilate enclosed areas.
- Evacuate all personnel not wearing protective equipment from areas of xylidine spill. Remove all sources of ignition and establish forced ventilation to keep vapor levels below explosive concentration (Pohanish, 2002).
- If a person is exposed to large amounts of xylidine, immediately relocate the affected person to an area of fresh air (NIOSH , 2002).
- Remain upwind of xylidine spills (AAR, 2000).
- AIHA ERPG Values for CAS1300-73-8 (AIHA, 2006):
- DOE TEEL Values for CAS1300-73-8 (U.S. Department of Energy, Office of Emergency Management, 2010):
- AEGL Values for CAS1300-73-8 (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; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2007; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2008; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2007; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2008; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2007; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2009; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2009; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2009; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2009; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2009; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2009; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2009; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2009; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2009; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2009; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2009; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2008; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2008; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2008; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2008; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2008; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2008; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2008; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2009; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2008; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2008; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2008; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2009; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2008; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2008; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2008; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2008; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2008; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2008; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2008; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2007; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2006; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2006; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2006; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2007; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2007; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2007; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2007; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2007; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2005; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2005; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2005; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2005; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2005; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2005; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2005; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2005; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2007; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2005; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2006; 62 FR 58840, 1997; 65 FR 14186, 2000; 65 FR 39264, 2000; 65 FR 77866, 2000; 66 FR 21940, 2001; 67 FR 7164, 2002; 68 FR 42710, 2003; 69 FR 54144, 2004):
- NIOSH IDLH Values for CAS1300-73-8 (National Institute for Occupational Safety and Health, 2007):
IDLH: 50 ppm Note(s): Not Listed
CONTAINMENT/WASTE TREATMENT OPTIONS
SPILL OR LEAK PRECAUTIONS - EMERGENCY RESPONSE GUIDEBOOK, GUIDE 153 (ERG, 2004) ELIMINATE all ignition sources (no smoking, flares, sparks or flames in immediate area). 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. 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 153 (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. fire situations ONLY; it is not effective in spill situations where direct contact with the substance is possible.
In case of a xylidine spill, immediately remove any sources of ignition. Evacuate any personnel who are not wearing protective clothing. Stop the leak if it can be done without endangering personnel (NFPA, 2002a; Pohanish, 2002). If a xylidine spill occurs on land, contain liquids by digging a holding pit, and stop the surface flow by using foamed polyurethane, foamed concrete or soil. Absorb the spilled liquid with vermiculite, cement powder, fly ash, dry sand or earth, peat, carbon, or commercial sorbents and deposit for later disposal. Do not wash spilled xylidine into sewers or other water intakes (AAR, 2000; ((ICSC, 1998)). If a xylidine spill occurs in water, use natural containment devices or spill control booms to prevent the contaminant from spreading. Extract trapped material with suction hoses (AAR, 2000).
Xylidine may be disposed of through incineration (HSDB , 2002; Pohanish, 2002). 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
Xylidine is released to the environment via various waste streams associated with its production, its use in the manufacture of various substances including pesticides, pharmaceuticals, polymers, and dyestuffs, and its use as a gasoline additive (HSDB, 2005).
- GENERAL POPULATION EXPOSURE
The general population may be exposed to xylidines through ingestion of contaminated drinking water (HSDB, 2005). It may be a natural component of Latakia pipe tobacco; xylidine isomers have been detected in its smoke (HSDB, 2005). Some exposure may occur through contact with commercial products containing xylidine residue, however, such exposure is not expected to be significant (HSDB, 2005).
ENVIRONMENTAL FATE AND KINETICS
When released into the environment, xylidine is expected to exist entirely in the vapor phase, where it is believed to degrade through reaction with photochemically-produced hydroxyl radicals and via direct photolysis (HSDB, 2005). Vapor phase xylidine degrades via reaction with photochemically-produced hydroxyl radicals (half-life: approx. 2.0 hours at an atmospheric concentration of 5 x 10(5) hydroxyl radicals/cm(3)) (HSDB, 2005). Direct photolysis in the atmosphere is possible because xylidine absorbs ultraviolet light in the environmental spectrum (HSDB, 2005). Xylidine is not expected to hydrolyze in the environment due to its lack of hydrolyzable functional groups (HSDB, 2005).
The estimated half-life of xylidine through reaction with photochemically produced hydroxyl radicals is approximately 2.0 hours (HSDB, 2005).
SURFACE WATER Based upon its classification as an aromatic amine, xylidine is expected to react rapidly in sunlit waters with photochemically-produced hydroxyl radicals and peroxy radicals, or to volatilize from water surfaces. However, in keeping with its aromatic amine characteristics, xylidine may adsorb strongly to suspended organic material in water. Hydrolysis and bioconcentration are not significant environmental fate processes (HSDB, 2005). In the water column, significant photooxidation of the compound due to hydroxyl and peroxy radicals may occur (half-life: 19-30 sunlight hours) (HSDB, 2005). The half-lives of xylidine in water, based on reaction with hydroxyl and peroxy radicals, are estimated at 19 and 30 sunlight hours, respectively. The rate constant for xylidine's vapor phase reaction with photochemically produced hydroxyl radicals is estimated at 2.0 x 10(-10) cm(3)/molecule-sec (at 25 degrees C) (HSDB, 2005). Volatilization half-lives range from 16 days in a model river to 120 days in a model lake (HSDB, 2005). Based on an estimated Henry's Law constant of 2.5 x 10(-6) atm-m(3)/mol, xylidine's volatilization half-lives from a model river (1 m deep, flowing 1 m/sec, wind velocity of 3 m/sec) and a model lake (1 m deep, flowing 0.05 m/sec, wind velocity of 0.5 m/sec) are estimated at approximately 16 days and 120 days, respectively (HSDB, 2005).
TERRESTRIAL Xylidine is expected to be moderately to highly mobile in soil, based on organic carbon partition coefficient (Koc) values of 52-240 for the six xylidine isomers ; however, in some soils, xylidine can be expected to bind to organic matter or humus, reducing its mobility. In pure clay minerals or soils at a neutral pH, xylidine exhibits low adsorption (HSDB, 2005). Xylidine may also undergo volatilization from moist soil surfaces, although it is not expected to volatilize from dry soil surfaces (HSDB, 2005). Xylidine may undergo biodegradation under aerobic conditions (HSDB, 2005).
ABIOTIC DEGRADATION
- In the atmosphere, xylidine exists primarily as a vapor and degrades via hydroxyl radical reaction and direct photolysis. In soils, the compound is expected to have medium to high mobility and may volatilize from moist surface soils. In aquatic systems, xylidine may adsorb to organic material or volatilize from surface waters. Reaction with hydroxyl and peroxy radicals may degrade the compound in sunlit waters (HSDB, 2005).
- Xylidine may be biodegraded in soils and water under aerobic conditions. Hydrolysis and bioconcentration are not expected to be significant (HSDB, 2005).
BIODEGRADATION
- Based on the results of a biodegradation study using river and sea water inoculum, xylidine (60 ppm) was found to be moderately to easily biodegraded (HSDB, 2005).
BIOACCUMULATION
ENVIRONMENTAL TOXICITY
- No information found at the time of this review.
-PHYSICAL/CHEMICAL PROPERTIES
MOLECULAR WEIGHT
DESCRIPTION/PHYSICAL STATE
- Xylidine exists as a pale yellow to brown liquid and possesses a weak, aromatic amine-like odor (ACGIH, 2001; NIOSH , 2002; Pohanish, 2002).
- There are six xylidine isomers (S Budavari , 2001). Technical grade xylidine is a varying mixture of the isomers of xylidine (2,4-, 2,5-, and 2,6-xylidine being the prominant isomers present) (ACGIH, 2001) Bingham et al, 2001). The commercial product primarily consists of the 2,4- and 2,6-isomers (Hathaway et al, 1996).
- Xylidine can be either a solid or a liquid, depending upon the isomers that comprise the mixture (AAR, 2000).
PH
VAPOR PRESSURE
- <1 mmHg (at 20 degrees C) (technical grade) (ACGIH, 2001; Bingham et al, 2001)
- 130 Pa (at 20 degrees C) ((ICSC, 1998))
SPECIFIC GRAVITY
- TEMPERATURE AND/OR PRESSURE NOT LISTED
0.97 - 0.99 (Bingham et al, 2001; S Budavari , 2001; (ICSC, 1998); ILO, 1998; Lewis, 2000; Lewis, 2001) 1.0 (technical grade) (ACGIH, 2001)
FREEZING/MELTING POINT
BOILING POINT
- 212 - 226 (technical grade) (ACGIH, 2001)
- 213 - 226 degrees C (Bingham et al, 2001; S Budavari , 2001; (ICSC, 1998); ILO, 1998; Lewis, 2000; Lewis, 2001; Pohanish, 2002)
- 415 - 439 degrees F (NIOSH , 2002)
FLASH POINT
- 94.5 degrees C (Bingham et al, 2001)
- 96.7 degrees C; 206 degrees F (ACGIH, 2001; Pohanish & Greene, 1997)
- 96 degrees C (closed cup) ((ICSC, 1998))
- 206 degrees F; 96.6 degrees C (closed cup) (Lewis, 2000; Lewis, 2001)
AUTOIGNITION TEMPERATURE
- 405 degrees C (ILO, 1998)
EXPLOSIVE LIMITS
SOLUBILITY
Xylidines are sparingly soluble in water (S Budavari , 2001). Insoluble (ACGIH, 2001) Slightly soluble (Bingham et al, 2001; ILO, 1998; Lewis, 2000; Lewis, 2001; NIOSH , 2002) Poor ((ICSC, 1998))
Soluble in alcohol (S Budavari , 2001; Lewis, 2000; Lewis, 2001) Soluble in ether and ethanol (Bingham et al, 2001; Lewis, 2001)
OCTANOL/WATER PARTITION COEFFICIENT
- log Pow = 1.8 (estimated) ((ICSC, 1998))
HENRY'S CONSTANT
SPECTRAL CONSTANTS
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