TRICHLORFON
HAZARDTEXT ®
Information to help in the initial response for evaluating chemical incidents
-IDENTIFICATION
SYNONYMS
TRICHLORFON PHOSPHONIC ACID, (2,2,2-TRICHLORO-1-HYDROXYETHYL)-, DIMETHYL ESTER AEROL 1 (PESTICIDE) AEROL 1 AGROFOROTOX ANTHON BAY 15922 BAYER 15922 BAYER L 13/59 BILARCIL BOVINOX BRITTEN BRITON CEKUFON CHLORFOS CHLORAK CHLOROFOS CHLOROFTALM CHLOROPHOS CHLOROPHTHALM CHLOROXYPHOS CICLOSOM CLOROFOS (Russian) CHLOROPHOSE COMBOT COMBOT EQUINE DANEX DEP DEP (PESTICIDE) DEPTHON DETF DIMETHOXY-2,2,2-TRICHLORO-1-HYDROXY-ETHYL-PHOSPHINE OXIDE O,O-DIMETHYL-(1-HYDROXY-2,2,2-TRICHLORAETHYL)PHOSPHONSAEURE ESTER (German) O,O-DIMETHYL-(1-HYDROXY-2,2,2-TRICHLORAETHYL)-PHOSPHAT (German) O,O-DIMETHYL-(1-HYDROXY-2,2,2-TRICHLORO)ETHYL PHOSPHATE DIMETHYL 1-HYDROXY-2,2,2-TRICHLOROETHYL PHOSPHONATE O,O-DIMETHYL (1-HYDROXY-2,2,2-TRICHLOROETHYL)PHOSPHONATE O,O-DIMETHYL-1-OXY-2,2,2-TRICHLOROETHYL PHOSPHONATE O,O-DIMETHYL-(2,2,2-TRICHLOOR-1-HYDROXY-ETHYL)-FOSFONAAT (Dutch) O,O-DIMETHYL-(2,2,2-TRICHLOR-1-HYDROXY-AETHYL)PHOSPHONAT (German) DIMETHYLTRICHLOROHYDROXYETHYL PHOSPHONATE DIMETHYL 2,2,2-TRICHLORO-1-HYDROXYETHYLPHOSPHONATE O,O-DIMETHYL-2,2,2-TRICHLORO-1-HYDROXYETHYL PHOSPHONATE O,O-DIMETIL 2,2,2-TRICHLORO-1-HIDROXIETIL FOSFONATO (Portugese) O,O-DIMETIL-(2,2,2-TRICLORO-1-IDROSSI-ETIL)-FOSFONATO (Italian) DIMETOX DIPTERAX DIPTEREX DIPTEREX 50 DIPTEVUR DITRIFON DYLOX DYLOX-METASYSTOX-R DYREX DYVON EQUINO-ACID EQUINO-AID FLIBOL E FLIEGENTELLER FOROTOX FOSCHLOR FOSCHLOR 25 FOSCHLOREM (Polish) FOSCHLOR R-50 1-HYDROXY-2,2,2-TRICHLORO-ETHYLE PHOSPHONATE DE DIMETHYLE (French) 1-HYDROXY-2,2,2-TRICHLOROETHYLPHOSPHONIC ACID DIMETHYL ESTER HYPODERMACID LEIVASOM LOISOL MASOTEN MAZOTEN METHYL CHLOROPHOS METIFONATE METRIFONATE METRIPHONATE NCI-C54831 NEGUVON NEGUVON A PHOSCHLOR PHOSCHLOR R50 PHOSPHONIC ACID, (1-HYDROXY-2,2,2-TRICHLOROETHYL)-, DIMETHYL ESTER POLFOSCHLOR PROXOL RICIFON RITSIFON SATOX 20WSC SOLDEP SOTIPOX TRICHLOORFON (Dutch) 2,2,2-TRICHLOROETHYL DIMETHYL PHOSPHATE TRICHLOROFON ((2,2,2-TRICHLORO-1-HYDROXYETHYL) DIMETHYLPHOSPHONATE) 2,2,2-TRICHLORO-1-HYDROXYETHYL-PHOSPHONATE, DIMETHYL ESTER (2,2,2-TRICHLORO-1-HYDROXYETHYL)PHOSPHONIC ACID DIMETHYL ESTER TRICHLOROPHON TRICHLORPHENE TRICHLORPHON TRICHLORPHON FN TRINEX TUGON TUGON FLY BAIT TUGON STABLE SPRAY VERMICIDE BAYER 2349 VOLFARTOL VOTEXIT WEC 50 WOTEXIT
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.
USES/FORMS/SOURCES
Trichlorfon has been used as a systemic insecticide and antihelminthic (Lewis, 1993; Budavari, 1996) to treat helminthiasis, including ankylostomiasis, ascariasis, trichuriasis, and creeping eruption in humans. Its pharmaceutical names are METRIFONATE or METRIPHONATE (Hayes & Laws, 1991). Trichlorfon is considered to be very toxic, with an estimated human oral lethal dose being 50 to 500 mg/kg, or between 1 teaspoon and 1 ounce for a 150-lb person (HSDB). A Romanian study estimated the acute lethal dose for humans to be about 25 mg (Apostol & Gavat, 1973). Pure trichlorfon is more toxic than the technical grade (Hayes & Laws, 1991).
Trichlorfon exists as white crystals which are soluble in water, chloroform, ether, benzene, and most chlorinated hydrocarbon solvents; it is insoluble in oils (Budavari, 1996; Lewis, 1993; Hayes & Laws, 1991). This compound is stable at room temperature, but decomposes at higher temperatures, in water, and at a pH less than 5.5 to form DICHLORVOS (Hayes & Laws, 1991). UV irradiation also produces dichlorvos and other degradation products (HSDB). It has persistent residues (Apostol & Gavat, 1973). TRICHLORFON (Phosphoric acid, (2,2,2-trichloro-1-hydroxyethyl)-, dimethyl ester) is an organophosphate pesticide with CHLOROPHOS and DIPTEREX as common trade names (HSDB). While it is generally classified as an organophosphate, trichlorfon is occasionally included among the organochlorine chemicals because of the chlorine groups present in its molecular structure. The toxic effects of trichlorfon also reflect both those of the organophosphates and of the organochlorines.
Trichlorfon is produced commercially as a 50% wettable powder, as 50%, 80% and 95% soluble powders, a 50% soluble concentrate, a 5% dust, 5% and 25% granules, and ultralow-volume 25%, 50%, and 75% concentrates (Hayes & Laws, 1991).
-CLINICAL EFFECTS
GENERAL CLINICAL EFFECTS
- The following are symptoms from organophosphates in general, which are due to the anticholinesterase activity of this class of compounds. All of these effects may not be documented for trichlorfon, but could potentially occur in individual cases.
- USES: Trichlorfon is an organophosphate insecticide.
- TOXICOLOGY: Organophosphates competitively inhibit pseudocholinesterase and acetylcholinesterase, preventing hydrolysis and inactivation of acetylcholine. Acetylcholine accumulates at nerve junctions, causing malfunction of the sympathetic, parasympathetic, and peripheral nervous systems and some of the CNS. Clinical signs of cholinergic excess develop.
- EPIDEMIOLOGY: Exposure to organophosphates is common, but serious toxicity is unusual in the US. Common source of severe poisoning in developing countries.
MILD TO MODERATE POISONING: MUSCARINIC EFFECTS: Can include bradycardia, salivation, lacrimation, diaphoresis, vomiting, diarrhea, urination, and miosis. NICOTINIC EFFECTS: Tachycardia, hypertension, mydriasis, and muscle cramps. SEVERE POISONING: MUSCARINIC EFFECTS: Bronchorrhea, bronchospasm, and acute lung injury. NICOTINIC EFFECTS: Muscle fasciculations, weakness, and respiratory failure. CENTRAL EFFECTS: CNS depression, agitation, confusion, delirium, coma, and seizures. Hypotension, ventricular dysrhythmias, metabolic acidosis, pancreatitis, and hyperglycemia can also develop. DELAYED EFFECTS: Intermediate syndrome is characterized by paralysis of respiratory, cranial motor, neck flexor, and proximal limb muscles 1 to 4 days after apparent recovery from cholinergic toxicity, and prior to the development of delayed peripheral neuropathy. Manifestations can include the inability to lift the neck or sit up, ophthalmoparesis, slow eye movements, facial weakness, difficulty swallowing, limb weakness (primarily proximal), areflexia, and respiratory paralysis. Recovery begins 5 to 15 days after onset. Distal sensory-motor polyneuropathy has been reported in several patients following exposure to trichlorfon. It may rarely develop 6 to 21 days following exposure. Characterized by burning or tingling followed by weakness beginning in the legs which then spreads proximally. In severe cases, it may result in spasticity or flaccidity. Recovery requires months and may not be complete. CHILDREN: May have different predominant signs and symptoms than adults (more likely CNS depression, stupor, coma, flaccidity, dyspnea, and seizures). Children may also have fewer muscarinic and nicotinic signs of intoxication (ie, secretions, bradycardia, fasciculations and miosis) as compared to adults. INHALATION EXPOSURE: Organophosphate vapors rapidly produce mucous membrane and upper airway irritation and bronchospasm, followed by systemic muscarinic, nicotinic and central effects if exposed to significant concentrations.
- POTENTIAL HEALTH HAZARDS - EMERGENCY RESPONSE GUIDEBOOK, GUIDE 152 (ERG, 2004)
Highly toxic, may be fatal if inhaled, swallowed or absorbed through skin. 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.
ACUTE CLINICAL EFFECTS
- Trichlorfon is considered to be very toxic, with an estimated human oral lethal dose being 50 to 500 mg/kg, or between 1 teaspoon and 1 ounce for a 150-lb person (HSDB). A Romanian study estimated the acute lethal dose for humans to be about 25 mg (Apostol & Gavat, 1973). Pure trichlorfon is more toxic than the technical grade (Hayes & Laws, 1991).
- Similar to other organophosphates, trichlorfon is a potent cholinesterase inhibitor (HSDB; (Hayes & Laws, 1991). Trichlorfon penetrates the skin (Trefilov, 1971), and deaths have been reported from rubbing trichlorfon (Chlorophoso) on the skin to cure scabies (Titova & Baduigin, 1970).
- A 29-year-old woman who drank 50 mL of trichlorfon experienced numbness of the entire body, muscular fibrillation, spasms of the extremities, difficulty swallowing, bronchospasm, dyspnea, nausea, vomiting of a green-colored liquid, increased salivation, vertigo, poor vision, marked overall weakness, and rigor (Plugatorenko, 1968).
- Soviet literature covering 662 poisoning cases reported cholinergic-type gastrointestinal disorders, psychomotor stimulation, muscular fibrillation, and miosis as signs of mild poisoning. Expiratory dyspnea, convulsions potentially leading to coma, pronounced miosis, and moderate hypotonia were listed as indicators of more severe poisoning (Titova & Baduigin, 1970).
- In contrast to other organophosphorus insecticides, acute exposure to trichlorfon can produce psychological effects resembling psychosis. Victims have experienced delirium, depression, anxiety, psychomotor stimulation, hallucinations, and delusions. Whether these effects are due to trichlorfon, an impurity, or the organochlorine moiety is unknown (Hayes & Laws, 1991).
- Trichlorfon has been associated with induction of polyneuropathy after acute exposures more than any other organophosphorus compound (Hayes & Laws, 1991). Onset of polyneuropathy can be as soon as 3 days after exposure, or as late as 26 days, and effects may be permanent or, at best, slow to resolve (Hayes & Laws, 1991).
- Chronic polyneuritis symptoms have persisted in humans following acute trichlorfon poisoning (Babchina, 1972; Kosik, 1968; Shutov & Varankina, 1969). This neurological effect has been confirmed in rats, where repeated dosing with trichlorfon caused increased excitability of the sciatic nerve. Because the early development of the electrophysiological changes caused no accompanying histological changes in the nerve, it was suggested that changes in nerve excitability may be a sensitive indicator of neurotoxicity (Georgiev, 1967).
- Rats given a single acute dose of 500 mg/kg suffered immunological depression lasting much longer than anticholinesterase poisoning symptoms (Gabliks, 1965).
CHRONIC CLINICAL EFFECTS
- A study of 110 workers chronically exposed to trichlorfon (Dipterex) reported muscular twitching, lightheadedness, breathlessness, and sweating as primary effects, with lightheadedness persisting for at least 4 months after exposure ceased. EEG abnormalities occurred among 35.5% of the workers during exposure and in 29.3% 4 months after exposure. Reduced blood cholinesterase activity was significant during exposure, but not 4 months later. In this study, EEG examinations were recommended as the best method for monitoring exposure to Dipterex (Lu, 1984).
- For the treatment of urinary bilharziasis, 10 male patients were administered 5 mg of trichlorfon (Dipterex) per kg once daily for 12 consecutive days and 1 mg of atropine sulfate 3 times daily to minimize side effects. Effects secondary to this treatment included chest pain, bronchial spasm, headache, tremors, vomiting, colic, fainting, and blurring of vision. Dipterex significantly depressed plasma cholinesterase. A plasma level of 0.4 mg of Dipterex per 100 mL depressed plasma cholinesterase by 50%, while at 2 mg/100 mL the level of cholinesterase was almost zero. Plasma cholinesterase depression began as early as 30 minutes after ingestion of the first dose and continued until at least 3 days after cessation of treatment (Hanna, 1966).
- Chronic gastric function disorders have also been reported in persons working with trichlorfon (Chlorophos) (Krasnyuk & Platonova, 1969).
- Trichlorfon (Chlorophos) was ten times more potent than radionuclides such as Cs-137, Az-65 and Ra-226 in suppressing normal immune function, inducing autoimmune responses, and in disrupting the normal spleen morphology in rats, mice, and rabbits (Shibik et al, 1976). Chronic oral administration (25 mg/kg for 4.5 months) induced immunological alterations beginning during the second week and persisting two months after treatment cessation, with no development of poisoning symptoms (Olefir, 1971). Human cells cultured in the presence of trichlorfon (Dipterex) were more susceptible to poliovirus infection (Gabliks, 1965).
- Several studies exist on the exploration of other physiologic effects of trichlorfon poisoning in experimental animals. Repeated administration in rats and dogs has been shown to reduce cholinesterase levels (Hayes & Laws, 1991). Subchronic exposure of rats to trichlorfon (10 ppm/day/90 days) led to loss of the circadian rhythms in levels of DNA, protein, and RNA content (Nicolau, 1983).
- Trichlorfon (Chlorophos) topically applied to the eyes of rats (0.5 and 1% solutions) increased permeability of blood vessels in the anterior portion of the eyes. Of three organophosphates tested, trichlorfon had the most prolonged effect and was the only compound which acted bilaterally, increasing the permeability of blood vessels in both the treated and untreated eyes (Korotkova, 1976). Abnormalities in vascular permeability were the greatest pathogenic change detected in rats inhaling trichlorfon at an airborne concentration of 0.2 to 1 mg/m(3) for 90 days (Bonashevskaya & Tabakova, 1972).
- Trichlorfon is not a sensitizer in experimental animals (Hayes & Laws, 1991).
-FIRST AID
FIRST AID AND PREHOSPITAL TREATMENT
Universal precautions should be followed by all individuals (i.e., first responders, emergency medical, and emergency department personnel) caring for the patient to avoid contamination. Nitrile gloves are suggested. Avoid direct contact with contaminated clothing, objects or body fluids. Vomiting containing organophosphates should be placed in a closed impervious container for proper disposal.
- DECONTAMINATION OF SPILLS/SUMMARY
A variety of methods have been described for organophosphate spill decontamination, most of which depend on changing the pH to promote hydrolysis to inactive phosphate diester compounds (EPA, 1978). The rate of hydrolysis depends on both the specific organophosphate compound involved and the increase in pH caused by the detoxicant used (EPA, 1978; EPA, 1975). NOTE: Do NOT use a MIXTURE of BLEACH and ALKALI for DECONTAMINATING ACEPHATE or ACETYL ORGANOPHOSPHATE COMPOUNDS such as ORTHENE(R). This can cause release of toxic acetyl chloride, acetylene, and phosgene gas. Spills of acephate organophosphates should be decontaminated by absorption and scrubbing with concentrated detergent (Ford JE, 1989).
Treatment of the spilled material with alkaline substances such as sodium carbonate (soda ash), sodium bicarbonate (baking soda), calcium hydroxide (slaked or hydrated lime), calcium hydroxide (lime or lime water, when in dilute solutions), and calcium carbonate (limestone) may be used for detoxification (EPA, 1975a). Chlorine-active compounds such as sodium hypochlorite (household bleach) or calcium hypochlorite (bleaching powder, chlorinated lime) may also be used to detoxify organophosphate spills (EPA, 1975a). While ammonia compounds have also been suggested as alternate detoxicants for organophosphate spills, UNDER NO CIRCUMSTANCES SHOULD AMMONIA EVER BE COMBINED WITH A CHLORINE-ACTIVE COMPOUND (BLEACH) AS HIGHLY IRRITATING CHLORAMINE GAS MAY BE EVOLVED.
- SMALL SPILL DECONTAMINATION
Three cups of Arm & Hammer washing soda (sodium carbonate) or Arm & Hammer baking soda (sodium bicarbonate) may be combined with one-half cup of household bleach and added to a plastic bucket of water. The washing soda is more alkaline and may be more efficacious, if available. Wear rubber gloves, and use a respirator certified effective against toxic vapors. Several washes may be required for decontamination (EPA, 1978). Spilled liquid may first be adsorbed with soil, sweeping compound, sawdust, or dry sand and then both the adsorbed material and the floor decontaminated with one of the above solutions (EPA, 1975a). NOTE: Do NOT use a COMBINATION of BLEACH and ALKALI to DECONTAMINATE ACEPHATE or ACETYL ORGANOPHOSPHATE COMPOUNDS such as ORTHENE(R). Spills involving acephate organophosphates should be decontaminated by the following procedure - Isolate and ventilate the area; keep sources of fire away; wear rubber or neoprene gloves and overshoes; get firefighting equipment ready; contain any liquid spill around the edge and absorb with Zorb-All(R) or similar material; dispose of absorbed or dry material in disposable containers; scrub the spilled area with concentrated detergent such as TIDE(R), ALL(R) or similar product; reabsorb scrubbing liquid and dispose as above; dispose of cleaning materials and contaminated clothing; wash gloves, overshoes and shovel with concentrated detergent. Call the National Pesticide Telecommunications Network for further assistance at 1-800-858-7378 or on the web at http://nptn.orst.edu.
- LARGE SPILL DECONTAMINATION
Sprinkle or spray the area with a mixture of one gallon of sodium hypochlorite (bleach) mixed with one gallon of water. Then spread calcium hydroxide (hydrated or slaked lime) liberally over the area and allow to stand for at least one hour (Pesticide User's Guide, 1976). Wear rubber gloves, and use a respirator certified effective against toxic vapors. Several washes may be required for decontamination (EPA, 1978). Other decontamination methods may be recommended by manufacturers of specific agents. Check containers, labels, or product literature for possible instructions regarding spill decontamination. NOTE: Do NOT USE a COMBINATION of BLEACH and ALKALI to DECONTAMINATE ACEPHATE or ACETYL ORGANOPHOSPHATE COMPOUNDS such as ORTHENE(R). Spills involving acephate organophosphates should be decontaminated by the following procedure - Isolate and ventilate the area; keep sources of fire away; wear rubber or neoprene gloves and overshoes; get fire-fighting equipment ready; contain any liquid spill around the edge and absorb with Zorb-All(R) or similar material; dispose of absorbed or dry material in disposable containers; scrub the spilled area with concentrated detergent such as TIDE(R), ALL(R) or similar product; re-absorb scrubbing liquid and dispose as above; dispose of cleaning materials and contaminated clothing; wash gloves, overshoes and shovel with concentrated detergent.
FURTHER CONTACT INFORMATION For further information contact the National Pesticide Telecommunications Network at 1-800-858-7378 or contact on the web at http://nptn.orst.edu. Disposal of large quantities or contamination of large areas may be regulated by various governmental agencies and reporting may be required. For small pesticide spills or for further information call the pesticide manufacturer or the National Pesticide Information Center (NPIC) at 1-800-858-7378. The National Response Center (NRC) is the federal point of contact for reporting of spills and can be reached at 1-800-424-8802. For those without 800 access, contact 202-267-2675. CHEMTREC can provide technical and hazardous materials information and can be reached at 1-800-424-9300 in the US; or 703-527-3887 outside the US.
-MEDICAL TREATMENT
LIFE SUPPORT
- Support respiratory and cardiovascular function.
SUMMARY
- FIRST AID - EMERGENCY RESPONSE GUIDEBOOK, GUIDE 152 (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.
ORAL EXPOSURE DERMAL EXPOSURE EYE EXPOSURE INHALATION EXPOSURE PERSONNEL PROTECTION Universal precautions should be followed by all individuals (i.e., first responders, emergency medical, and emergency department personnel) caring for the patient to avoid contamination. Nitrile gloves are suggested. Avoid direct contact with contaminated clothing, objects or body fluids. Vomiting containing organophosphates should be placed in a closed impervious container for proper disposal.
DECONTAMINATION OF SPILLS/SUMMARY A variety of methods have been described for organophosphate spill decontamination, most of which depend on changing the pH to promote hydrolysis to inactive phosphate diester compounds (EPA, 1978). The rate of hydrolysis depends on both the specific organophosphate compound involved and the increase in pH caused by the detoxicant used (EPA, 1978; EPA, 1975). NOTE: Do NOT use a MIXTURE of BLEACH and ALKALI for DECONTAMINATING ACEPHATE or ACETYL ORGANOPHOSPHATE COMPOUNDS such as ORTHENE(R). This can cause release of toxic acetyl chloride, acetylene, and phosgene gas. Spills of acephate organophosphates should be decontaminated by absorption and scrubbing with concentrated detergent (Ford JE, 1989).
Treatment of the spilled material with alkaline substances such as sodium carbonate (soda ash), sodium bicarbonate (baking soda), calcium hydroxide (slaked or hydrated lime), calcium hydroxide (lime or lime water, when in dilute solutions), and calcium carbonate (limestone) may be used for detoxification (EPA, 1975a). Chlorine-active compounds such as sodium hypochlorite (household bleach) or calcium hypochlorite (bleaching powder, chlorinated lime) may also be used to detoxify organophosphate spills (EPA, 1975a). While ammonia compounds have also been suggested as alternate detoxicants for organophosphate spills, UNDER NO CIRCUMSTANCES SHOULD AMMONIA EVER BE COMBINED WITH A CHLORINE-ACTIVE COMPOUND (BLEACH) AS HIGHLY IRRITATING CHLORAMINE GAS MAY BE EVOLVED.
SMALL SPILL DECONTAMINATION Three cups of Arm & Hammer washing soda (sodium carbonate) or Arm & Hammer baking soda (sodium bicarbonate) may be combined with one-half cup of household bleach and added to a plastic bucket of water. The washing soda is more alkaline and may be more efficacious, if available. Wear rubber gloves, and use a respirator certified effective against toxic vapors. Several washes may be required for decontamination (EPA, 1978). Spilled liquid may first be adsorbed with soil, sweeping compound, sawdust, or dry sand and then both the adsorbed material and the floor decontaminated with one of the above solutions (EPA, 1975a). NOTE: Do NOT use a COMBINATION of BLEACH and ALKALI to DECONTAMINATE ACEPHATE or ACETYL ORGANOPHOSPHATE COMPOUNDS such as ORTHENE(R). Spills involving acephate organophosphates should be decontaminated by the following procedure - Isolate and ventilate the area; keep sources of fire away; wear rubber or neoprene gloves and overshoes; get firefighting equipment ready; contain any liquid spill around the edge and absorb with Zorb-All(R) or similar material; dispose of absorbed or dry material in disposable containers; scrub the spilled area with concentrated detergent such as TIDE(R), ALL(R) or similar product; reabsorb scrubbing liquid and dispose as above; dispose of cleaning materials and contaminated clothing; wash gloves, overshoes and shovel with concentrated detergent. Call the National Pesticide Telecommunications Network for further assistance at 1-800-858-7378 or on the web at http://nptn.orst.edu.
LARGE SPILL DECONTAMINATION Sprinkle or spray the area with a mixture of one gallon of sodium hypochlorite (bleach) mixed with one gallon of water. Then spread calcium hydroxide (hydrated or slaked lime) liberally over the area and allow to stand for at least one hour (Pesticide User's Guide, 1976). Wear rubber gloves, and use a respirator certified effective against toxic vapors. Several washes may be required for decontamination (EPA, 1978). Other decontamination methods may be recommended by manufacturers of specific agents. Check containers, labels, or product literature for possible instructions regarding spill decontamination. NOTE: Do NOT USE a COMBINATION of BLEACH and ALKALI to DECONTAMINATE ACEPHATE or ACETYL ORGANOPHOSPHATE COMPOUNDS such as ORTHENE(R). Spills involving acephate organophosphates should be decontaminated by the following procedure - Isolate and ventilate the area; keep sources of fire away; wear rubber or neoprene gloves and overshoes; get firefighting equipment ready; contain any liquid spill around the edge and absorb with Zorb-All(R) or similar material; dispose of absorbed or dry material in disposable containers; scrub the spilled area with concentrated detergent such as TIDE(R), ALL(R) or similar product; reabsorb scrubbing liquid and dispose as above; dispose of cleaning materials and contaminated clothing; wash gloves, overshoes and shovel with concentrated detergent.
FURTHER CONTACT INFORMATION For further information contact the National Pesticide Telecommunications Network at 1-800-858-7378 or contact on the web at http://nptn.orst.edu. Disposal of large quantities or contamination of large areas may be regulated by various governmental agencies and reporting may be required. For small pesticide spills or for further information call the pesticide manufacturer or the National Pesticide Information Center (NPIC) at 1-800-858-7378. The National Response Center (NRC) is the federal point of contact for reporting of spills and can be reached at 1-800-424-8802. For those without 800 access, contact 202-267-2675. CHEMTREC can provide technical and hazardous materials information and can be reached at 1-800-424-9300 in the US; or 703-527-3887 outside the US.
ANTIDOTES
-RANGE OF TOXICITY
MAXIMUM TOLERATED EXPOSURE
- The World Health Organization (WHO) has classified trichlorfon as pesticide class II (moderately hazardous) (World Health Organization, 2006).
- Carcinogenicity Ratings for CAS52-68-6 :
ACGIH (American Conference of Governmental Industrial Hygienists, 2010): A4 ; Listed as: Trichlorphon 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): 3 ; Listed as: Trichlorfon 3 : The agent (mixture or exposure circumstance) is not classifiable as to its carcinogenicity to humans. This category is used most commonly for agents, mixtures and exposure circumstances for which the evidence of carcinogenicity is inadequate in humans and inadequate or limited in experimental animals. Exceptionally, agents (mixtures) for which the evidence of carcinogenicity is inadequate in humans but sufficient in experimental animals may be placed in this category when there is strong evidence that the mechanism of carcinogenicity in experimental animals does not operate in humans. Agents, mixtures and exposure circumstances that do not fall into any other group are also placed in this category.
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 CAS52-68-6 (U.S. Environmental Protection Agency, 2011):
-STANDARDS AND LABELS
WORKPLACE STANDARDS
- ACGIH TLV Values for CAS52-68-6 (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 CAS52-68-6 (AIHA, 2006):
- NIOSH REL and IDLH Values for CAS52-68-6 (National Institute for Occupational Safety and Health, 2007):
- OSHA PEL Values for CAS52-68-6 (U.S. Occupational Safety, and Health Administration (OSHA), 2010):
- OSHA List of Highly Hazardous Chemicals, Toxics, and Reactives for CAS52-68-6 (U.S. Occupational Safety and Health Administration, 2010):
ENVIRONMENTAL STANDARDS
- EPA CERCLA, Hazardous Substances and Reportable Quantities for CAS52-68-6 (U.S. Environmental Protection Agency, 2010):
- EPA CERCLA, Hazardous Substances and Reportable Quantities, Radionuclides for CAS52-68-6 (U.S. Environmental Protection Agency, 2010):
- EPA RCRA Hazardous Waste Number for CAS52-68-6 (U.S. Environmental Protection Agency, 2010b):
- EPA SARA Title III, Extremely Hazardous Substance List for CAS52-68-6 (U.S. Environmental Protection Agency, 2010):
- EPA SARA Title III, Community Right-to-Know for CAS52-68-6 (40 CFR 372.65, 2006; 40 CFR 372.28, 2006):
Listed as: Trichlorfon [Phosphonic acid, (2,2,2-trichloro-1-hydroxyethyl)-, dimethyl ester] Effective Date for Reporting Under 40 CFR 372.30: 1/1/87 Lower Thresholds for Chemicals of Special Concern under 40 CFR 372.28:
- DOT List of Marine Pollutants for CAS52-68-6 (49 CFR 172.101 - App. B, 2005):
- EPA TSCA Inventory for CAS52-68-6 (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 CAS52-68-6 (NFPA, 2002):
-PERSONAL PROTECTION
SUMMARY
- RECOMMENDED PROTECTIVE CLOTHING - EMERGENCY RESPONSE GUIDEBOOK, GUIDE 152 (ERG, 2004)
Wear positive pressure self-contained breathing apparatus (SCBA). Wear chemical protective clothing that is specifically recommended by the manufacturer. It may provide little or no thermal protection. Structural firefighters' protective clothing provides limited protection in fire situations ONLY; it is not effective in spill situations where direct contact with the substance is possible.
PROTECTIVE CLOTHING
- CHEMICAL PROTECTIVE CLOTHING. Search results for CAS 52-68-6.
-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 152 (ERG, 2004) Combustible material: may burn but does not ignite readily. Containers may explode when heated. Runoff may pollute waterways. Substance may be transported in a molten form.
- FLAMMABILITY CLASSIFICATION
- NFPA Flammability Rating for CAS52-68-6 (NFPA, 2002):
- FIRE CONTROL/EXTINGUISHING AGENTS
- SMALL FIRE PRECAUTIONS - EMERGENCY RESPONSE GUIDEBOOK, GUIDE 152 (ERG, 2004)
- LARGE FIRE PRECAUTIONS - EMERGENCY RESPONSE GUIDEBOOK, GUIDE 152 (ERG, 2004)
Water spray, fog or regular foam. Move containers from fire area if you can do it without risk. Dike fire control water for later disposal; do not scatter the material. Use water spray or fog; do not use straight streams.
- TANK OR CAR/TRAILER LOAD FIRE PRECAUTIONS - EMERGENCY RESPONSE GUIDEBOOK, GUIDE 152 (ERG, 2004)
Fight fire from maximum distance or use unmanned hose holders or monitor nozzles. Do not get water inside containers. Cool containers with flooding quantities of water until well after fire is out. Withdraw immediately in case of rising sound from venting safety devices or discoloration of tank. ALWAYS stay away from tanks engulfed in fire. For massive fire, use unmanned hose holders or monitor nozzles; if this is impossible, withdraw from area and let fire burn.
- NFPA Extinguishing Methods for CAS52-68-6 (NFPA, 2002):
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 152 (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 152 (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 152 (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.
- AIHA ERPG Values for CAS52-68-6 (AIHA, 2006):
- DOE TEEL Values for CAS52-68-6 (U.S. Department of Energy, Office of Emergency Management, 2010):
- AEGL Values for CAS52-68-6 (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 CAS52-68-6 (National Institute for Occupational Safety and Health, 2007):
CONTAINMENT/WASTE TREATMENT OPTIONS
SPILL OR LEAK PRECAUTIONS - EMERGENCY RESPONSE GUIDEBOOK, GUIDE 152 (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. Cover with plastic sheet to prevent spreading. Absorb or cover with dry earth, sand or other non-combustible material and transfer to containers. DO NOT GET WATER INSIDE CONTAINERS.
RECOMMENDED PROTECTIVE CLOTHING - EMERGENCY RESPONSE GUIDEBOOK, GUIDE 152 (ERG, 2004) Wear positive pressure self-contained breathing apparatus (SCBA). Wear chemical protective clothing that is specifically recommended by the manufacturer. It may provide little or no thermal protection. Structural firefighters' protective clothing provides limited protection in fire situations ONLY; it is not effective in spill situations where direct contact with the substance is possible.
-PHYSICAL/CHEMICAL PROPERTIES
MOLECULAR WEIGHT
DESCRIPTION/PHYSICAL STATE
- Trichlorfon exists as colorless, white, or pale yellow crystals (HSDB, 2004).
VAPOR PRESSURE
- 7.8 x 10(-6) mmHg (at 20 degrees C) (HSDB, 2004)
SPECIFIC GRAVITY
- OTHER TEMPERATURE AND/OR PRESSURE
FREEZING/MELTING POINT
BOILING POINT
- 100 degrees C (at 1 mmHg) (HSDB, 2004)
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