MOBILE VIEW  | 

METHYLENE CHLORIDE

Classification   |    Detailed evidence-based information

Therapeutic Toxic Class

    A) Methylene chloride, a halogenated hydrocarbon and solvent, is an irritant and CNS depressant.

Specific Substances

    1) AEROTHENE MM
    2) CHLORURE DE METHYLENE (French)
    3) DCM
    4) Dichloromethane
    5) MDC
    6) METHANE DICHLORIDE
    7) METHANE, DICHLORO-
    8) Methylene bichloride
    9) Methylene dichloride
    10) METHYLENUM CHLORATUM
    11) METYLENU CHLOREK (Polish)
    12) NARKOTIL
    13) R 30
    14) SOLAESTHIN
    15) SOLMETHINE
    16) CAS 75-09-2
    17) References: Hathaway et al, 1996
    18) DCM (METHYLENE CHLORIDE)
    19) METHYLENU CHLOREK (POLISH)
    1.2.1) MOLECULAR FORMULA
    1) CH2Cl2 ClCH2Cl

Available Forms Sources

    A) FORMS
    1) Methylene chloride is a colorless, volatile, nearly nonflammable liquid (Budavari, 2000; Lewis, 2000; AAR, 2000).
    2) Because methylene chloride hydrolyses slowly if moisture is present, commercial grades normally contain a small amount of stabilizer to prevent decomposition (IPCS, 1996).
    3) In one study, 42 bathtub stripping products from the Internet and several hardware stores contained 60% to 100% methylene chloride. OSHA has reported 13 bathtub refinisher fatalities associated with methylene chloride stripping agents in 9 states from 2000 to 2011. Blood methylene chloride concentrations of 6 patients ranged from 18 to 223 mg/L (Centers for Disease Control and Prevention (CDC), 2012).
    B) SOURCES
    1) It is produced by the chlorination of methyl chloride followed by distillation, by thermal chlorination (methyl chloride + chlorine), by Lummus oxychlorination (natural gas + hydrogen chloride), or by oxychlorination (natural gas + anhydrous hydrogen chloride) (Ashford, 1994; Lewis, 1997).
    2) The Stauffer process is used to produce methylene chloride. In this process, methanol is reacted with hydrogen chloride and then chlorine. Byproducts include chloroform and carbon tetrachloride (IPCS, 1996).

Life Support

    A) This overview assumes that basic life support measures have been instituted.

Clinical Effects

    0.2.1) SUMMARY OF EXPOSURE
    A) USES: Dichloromethane (methylene chloride) is used as a solvent in the chemical industry. In household products, it is used as paint remover, aerosol propellant, urethane foam, and degreaser.
    B) TOXICOLOGY: Similar to other halogenated solvents, an acute high concentration exposure can cause CNS depression and respiratory depression. Dichloromethane is a tissue irritant, and a high concentration inhalation may cause mucous membrane irritation, pulmonary edema, and hemorrhage. It is metabolized to carbon monoxide (CO) and large exposures can lead to elevated carboxyhemoglobin concentrations. When heated to decomposition, dichloromethane releases toxic phosgene, hydrogen chloride gas, and chlorine gas.
    C) EPIDEMIOLOGY: Poisoning is rare and most often occurs by the inhalational route. Rarely, intentional ingestions have been reported. Systemic poisoning after dermal exposure is unusual since dichloromethane evaporates quickly.
    D) WITH POISONING/EXPOSURE
    1) MILD TO MODERATE TOXICITY: Drowsiness, somnolence, skin and mucous membrane irritation, abdominal pain if ingested, and nausea and vomiting.
    2) SEVERE TOXICITY: Severe effects include significant CNS depression, corrosive injury of the gastrointestinal tract, and pancreatitis. Hepatotoxicity, renal injury leading to renal failure may be seen, but are not common. Elevated carboxyhemoglobin levels may develop in significant poisoning. Severe inhalational injury is associated with pulmonary edema and hemorrhage. Hypotension and hypertension have been reported after a large, deliberate ingestion. Cardiac dysrhythmias and cardiac depression have been linked to chronic exposure with dichloromethane. Delirium and seizures may be seen.
    0.2.4) HEENT
    A) WITH POISONING/EXPOSURE
    1) Exposure to fumes causes eye irritation. Direct contact or immersion may cause burns to the cornea or oral mucosa.
    0.2.5) CARDIOVASCULAR
    A) WITH POISONING/EXPOSURE
    1) Methylene chloride may cause occupational heart disease. Inhalation of methylene chloride may exacerbate angina in persons with preexisting cardiac disease.
    2) Angina, myocardial infarction, and cardiac arrest associated with methylene chloride inhalation developed in one patient. Hypotension, hypertension, and tachycardia have been reported after ingestion of methylene chloride.
    0.2.6) RESPIRATORY
    A) WITH POISONING/EXPOSURE
    1) Pulmonary irritation and cough may develop after inhalation exposure. Pulmonary edema is rarely reported. Respiratory failure may develop secondary to CNS depression in severe exposures. Goodpasture's syndrome has been associated with one case of occupational exposure.
    0.2.7) NEUROLOGIC
    A) WITH POISONING/EXPOSURE
    1) Headache and light-headedness are common after inhalation. Psychomotor performance is impaired with acute exposure. Syncope, CNS depression and coma may develop with more severe exposure. CNS excitation including seizures may also occur.
    0.2.8) GASTROINTESTINAL
    A) WITH POISONING/EXPOSURE
    1) Nausea and vomiting are common after inhalation exposure. Gastrointestinal ulceration and bleeding and pancreatitis have been reported after ingestion.
    0.2.9) HEPATIC
    A) WITH POISONING/EXPOSURE
    1) Elevated liver enzyme levels rarely occur.
    0.2.10) GENITOURINARY
    A) WITH POISONING/EXPOSURE
    1) Renal effects are rare. Hematuria, acute tubular necrosis and the development of Goodpasture's syndrome have been associated with exposure to methylene chloride.
    0.2.13) HEMATOLOGIC
    A) WITH POISONING/EXPOSURE
    1) Methylene chloride is metabolized to carbon monoxide. Carboxyhemoglobin as high as 50% are reported, and levels may continue to rise for several hours after exposure has ceased. The apparent half-life of carboxyhemoglobin is prolonged to 13 hours because of ongoing production of carboxyhemoglobin.
    0.2.14) DERMATOLOGIC
    A) WITH POISONING/EXPOSURE
    1) Skin irritation, pain, numbness and mild burns may develop with acute exposure. Severe burns may develop with prolonged exposure or immersion. Systemic effects can result from absorption through the skin.
    0.2.18) PSYCHIATRIC
    A) Delirium with auditory and visual hallucinations is rare but has been reported after chronic exposure.
    0.2.20) REPRODUCTIVE
    A) Methylene chloride was not found to be teratogenic in mice and rabbits. It crosses the placenta, and is found in breast milk, and has been associated with increased spontaneous abortion. However, few reproductive effects are seen in rats.
    0.2.21) CARCINOGENICITY
    A) Methylene chloride has been classified as probably carcinogenic to humans (Group 2A) by IARC following a systematic review and evaluation.

Laboratory Monitoring

    A) Monitor vital signs and mental status.
    B) Order carboxyhemoglobin levels.
    C) Routine lab studies include: serum electrolytes, renal function, liver enzymes and lipase. Obtain arterial blood gases when significant pulmonary toxicity is observed.
    D) Dichloromethane concentrations are not rapidly available or useful to guide therapy.

Treatment Overview

    0.4.2) ORAL/PARENTERAL EXPOSURE
    A) MANAGEMENT OF MILD TO MODERATE TOXICITY
    1) Treatment is symptomatic and supportive. Remove contaminated clothing, wash exposed skin with soap and water. Administer supplemental oxygen for possible carbon monoxide (CO) formation. EYE EXPOSURE: Irrigate with saline or water.
    B) MANAGEMENT OF SEVERE TOXICITY
    1) Orotracheal intubation for airway protection should be considered in patients with severe CNS depression. Administer 100% oxygen for possible CO poisoning. In patients with significant CNS toxicity and elevated carboxyhemoglobin levels, consider hyperbaric oxygen therapy. Treat seizures and delirium with benzodiazepines. Treat ongoing vomiting with antiemetics.
    C) DECONTAMINATION
    1) PREHOSPITAL: Activated charcoal is not recommended because of limited efficacy, rapid absorption of dichloromethane after ingestion, and the risk of corrosive injury to the gastrointestinal tract.
    2) HOSPITAL: Activated charcoal is not recommended because of limited efficacy, rapid absorption of dichloromethane after ingestion, and the risk of corrosive injury to the gastrointestinal tract. Consider nasogastric suction, if the patient presents early (0.5 to 2 hours) after a very large oral ingestion.
    D) AIRWAY MANAGEMENT
    1) Administer high flow oxygen to any symptomatic patient. Patients with significant CNS depression or pulmonary injury need orotracheal intubation and mechanical ventilation. Consider significant oropharyngeal injury after large ingestions.
    E) ANTIDOTE
    1) There is no antidote for methylene chloride poisoning.
    F) PATIENT DISPOSITION
    1) HOME CRITERIA: Asymptomatic adults and children can be kept home after an inadvertent dermal or inhalation exposure or taste ingestions with dichloromethane household products. Any patient with a significant industrial exposure or an intentional ingestion should be admitted.
    2) ADMISSION CRITERIA: A patient with signs of CNS toxicity, significant gastrointestinal symptoms, mucous membrane irritation, and any patient with an intentional exposure should be admitted.
    3) CONSULT CRITERIA: Consult a poison center or medical toxicologist for assistance in managing patients with severe toxicity (ie, CNS depression, organ failure, significant CO poisoning), or in whom the diagnosis is unclear.
    G) PITFALLS
    1) Dichloromethane poisoning may lead to significant endogenous CO poisoning. Half-life of carboxyhemoglobin is prolonged to about 13 hours in dichloromethane poisoning due to ongoing formation of CO in the body.
    H) DIFFERENTIAL DIAGNOSIS
    1) Consider poisoning with other hydrocarbons, CNS depressants, and acetaminophen in the case of hepatotoxicity.
    0.4.3) INHALATION EXPOSURE
    A) Move patient to fresh air; administer 100% oxygen; determine carboxyhemoglobin concentration if symptomatic.
    B) ACUTE LUNG INJURY: Maintain ventilation and oxygenation and evaluate with frequent arterial blood gases and/or pulse oximetry monitoring. Early use of PEEP and mechanical ventilation may be needed.
    0.4.4) EYE EXPOSURE
    A) 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.
    0.4.5) DERMAL EXPOSURE
    A) OVERVIEW
    1) 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).
    2) Administer oxygen and determine carboxyhemoglobin concentration in patients with systemic symptoms.

Range Of Toxicity

    A) TOXICITY: Inhalation is the usual route of occupational exposure. OSHA's short-term exposure limit: 125 ppm; 8-hour permissible exposure limit: 25 ppm; NIOSH immediately dangerous to life and health concentration: 2300 ppm. For humans, 50,000 ppm is considered life-threatening. The lowest oral dose reported to cause death is 357 mg/kg.
    B) Patients usually develop toxicity after ingestions of more than 25 mL of dichloromethane.
    C) Methylene chloride is metabolized to carbon monoxide, resulting in carboxyhemoglobin in the blood and toxic effects. When heated to decomposition, methylene chloride releases toxic phosgene, hydrogen chloride gas, and chlorine gas.

Summary Of Exposure

    A) USES: Dichloromethane (methylene chloride) is used as a solvent in the chemical industry. In household products, it is used as paint remover, aerosol propellant, urethane foam, and degreaser.
    B) TOXICOLOGY: Similar to other halogenated solvents, an acute high concentration exposure can cause CNS depression and respiratory depression. Dichloromethane is a tissue irritant, and a high concentration inhalation may cause mucous membrane irritation, pulmonary edema, and hemorrhage. It is metabolized to carbon monoxide (CO) and large exposures can lead to elevated carboxyhemoglobin concentrations. When heated to decomposition, dichloromethane releases toxic phosgene, hydrogen chloride gas, and chlorine gas.
    C) EPIDEMIOLOGY: Poisoning is rare and most often occurs by the inhalational route. Rarely, intentional ingestions have been reported. Systemic poisoning after dermal exposure is unusual since dichloromethane evaporates quickly.
    D) WITH POISONING/EXPOSURE
    1) MILD TO MODERATE TOXICITY: Drowsiness, somnolence, skin and mucous membrane irritation, abdominal pain if ingested, and nausea and vomiting.
    2) SEVERE TOXICITY: Severe effects include significant CNS depression, corrosive injury of the gastrointestinal tract, and pancreatitis. Hepatotoxicity, renal injury leading to renal failure may be seen, but are not common. Elevated carboxyhemoglobin levels may develop in significant poisoning. Severe inhalational injury is associated with pulmonary edema and hemorrhage. Hypotension and hypertension have been reported after a large, deliberate ingestion. Cardiac dysrhythmias and cardiac depression have been linked to chronic exposure with dichloromethane. Delirium and seizures may be seen.

Heent

    3.4.1) SUMMARY
    A) WITH POISONING/EXPOSURE
    1) Exposure to fumes causes eye irritation. Direct contact or immersion may cause burns to the cornea or oral mucosa.
    3.4.3) EYES
    A) WITH POISONING/EXPOSURE
    1) IRRITATION: Vapor exposure can produce conjunctivitis and lacrimation (Hathaway et al, 1996).
    2) CORNEAL BURNS: Splash contact may produce immediate pain but significant corneal injury does not usually result (Grant & Schuman, 1993; (ACGIH, 1991). Immersion has produced severe corneal burns (Hall & Rumack, 1990).
    3.4.5) NOSE
    A) WITH POISONING/EXPOSURE
    1) Exposure to methylene chloride can result in nasal discharge (Harbison, 1998).
    3.4.6) THROAT
    A) WITH POISONING/EXPOSURE
    1) BURNS: Oral mucosal burns with erythema and blistering have been reported after ingestion (Roberts & Marshall, 1976).
    2) Sore throat and dry mouth have been reported after ingestion (Chang et al, 1999).
    3) Throat irritation was reported following inhalational exposure to methylene chloride vapors (Jacubovich et al, 2005).

Cardiovascular

    3.5.1) SUMMARY
    A) WITH POISONING/EXPOSURE
    1) Methylene chloride may cause occupational heart disease. Inhalation of methylene chloride may exacerbate angina in persons with preexisting cardiac disease.
    2) Angina, myocardial infarction, and cardiac arrest associated with methylene chloride inhalation developed in one patient. Hypotension, hypertension, and tachycardia have been reported after ingestion of methylene chloride.
    3.5.2) CLINICAL EFFECTS
    A) CARDIOVASCULAR FINDING
    1) WITH POISONING/EXPOSURE
    a) Methylene chloride is suspected of causing occupational heart disease, including coronary atherosclerosis, dysrhythmias and myopathy (Clayton & Clayton, 1994). Methylene chloride is also reported to produce engorgement of blood vessels of the brain and dilation of the heart (ILO, 1998).
    b) CASE REPORT: A 24-year-old man was found unconscious 6.5 hours after applying one gallon of paint stripper (containing 70% to 85% dichloromethane, methanol, isopropyl alcohol, 2-butoxyethanol, and ethanol) to the floor of a baptismal font in a church. He did not respond to resuscitative efforts and was pronounced dead. During an autopsy, cardiomegaly with 4-chamber dilatation and coronary atherosclerosis with 50% occlusion of the left anterior descending artery were observed. Postmortem laboratory results showed a COHb of 10% and a blood dichloromethane concentration of 37.8 mg/dL. It was determined that dichloromethane poisoning, resulting in hypoxia and dysrhythmias, was the cause of death (Macisaac et al, 2013).
    B) MYOCARDIAL INFARCTION
    1) WITH POISONING/EXPOSURE
    a) Myocardial ischemia and infarction related to methylene chloride use were reported (Harbison, 1998).
    b) CASE REPORT - A 66-year-old man developed chest pain on three separate occasions after working with methylene chloride based paint remover in a poorly ventilated room. On the first two occasions he sustained acute myocardial infarctions; the second infarction was complicated by cardiogenic shock, dysrhythmias and congestive heart failure. On the third occasion he sustained a cardiac arrest prior to the arrival of paramedics (Stewart & Hake, 1976). Carboxyhemoglobin levels were not reported.
    C) HYPOTENSIVE EPISODE
    1) WITH POISONING/EXPOSURE
    a) Hypotension followed by hypertension was reported in two patients after ingesting 300 to 350 mL methylene chloride (Chang et al, 1999).
    D) HYPERTENSIVE EPISODE
    1) WITH POISONING/EXPOSURE
    a) Hypertension was reported in 3 of 6 patients who ingested 100 to 350 mL of methylene chloride (Chang et al, 1999).
    E) TACHYARRHYTHMIA
    1) WITH POISONING/EXPOSURE
    a) Tachycardia (heart rate: 110 to 126 beats per minute) was reported in two patients following ingestion of 300 mL and 75 mL methylene chloride, respectively. The patient who had ingested 300 mL became comatose and died 9 days after ingestion (Chang et al, 1999).
    F) SYNCOPE
    1) WITH POISONING/EXPOSURE
    a) Syncope has been reported (Fagin et al, 1980).
    G) CARDIORESPIRATORY ARREST
    1) WITH POISONING/EXPOSURE
    a) CASE REPORT: A 52-year-old man with a history of hyperlipidemia experienced a sudden cardiorespiratory arrest after refinishing a bathtub with an aircraft paint stripper (Tal-Strip II Aircraft coating remover) containing 60% to 100% methylene chloride. Resuscitation attempts were not successful Laboratory results revealed a blood methylene chloride concentration of 50 mg/L. An autopsy showed mild coronary atherosclerosis and mucus plugging of bronchi and bronchioles. It was estimated that 6 fluid ounces (177 mL) of methylene chloride-based stripper was used during a similar job and methylene chloride vapor concentration of 92,949 to 154,916 ppm in the bathtub and 5099 to 8499 ppm in the bathroom were estimated. It was determined that this patient was exposed to 637 to 1062 ppm of methylene chloride in the bathroom and 11,618 to 19,364 ppm of methylene chloride in the tub during 1 hour of exposure (OSHA's short-term exposure limit: 125 ppm; 8-hour permissible exposure limit: 25 ppm; NIOSH immediately dangerous to life and health level: 2300 ppm). An investigation revealed that at least 13 professional bathtub refinishers died while using methylene chloride based products on bathtubs in bathrooms with inadequate ventilation between the years 2000 and 2010 (Centers for Disease Control and Prevention (CDC), 2012).
    H) TOBACCO USE AND EXPOSURE - FINDING
    1) WITH POISONING/EXPOSURE
    a) Smokers who have a history of angina or coronary artery disease, and who have moderate or high methylene chloride exposure may be at risk of adverse cardiovascular effects. Smokers exposed to the methylene chloride vapor concentrations equal to or exceeding the current permissible workplace exposure limit have had carboxyhemoglobin levels of 15% or greater (US DHHS, 1990).
    I) LACK OF EFFECT
    1) CASE SERIES - Ott et al (1983) reported that there was no apparent increase in ventricular ectopy, supraventricular ectopy or ST depression in 24 workers exposed to methylene chloride at a time-weighted average which ranged from 60 to 475 ppm, compared with 26 unexposed workers. The unexposed reference group had a higher number of smokers and individuals with heart disease than the exposed worker group (Ott et al, 1983).
    2) Based on the available studies, it has been concluded that the cardiovascular system is not a target for methylene chloride toxicity in humans under typical inhalational exposure conditions. Some adverse effects have been reported in animals at doses which may not be relevant to human exposures (US DHHS, 1993).
    3) CASE SERIES - No excess risk of death due to ischemic heart disease was reported in a cohort study (1964 to 1988) of 1,013 workers chronically exposed to methylene chloride (Hearne et al, 1990).
    4) CASE SERIES - No statistically significant excessive reports of exercise-induced chest discomfort or heartbeat irregularities were reported by 150 workers chronically exposed to methylene chloride (average 475 ppm for an 8 hr TWA over 10 or more years) as compared to nonexposed workers (Soden, 1993).

Respiratory

    3.6.1) SUMMARY
    A) WITH POISONING/EXPOSURE
    1) Pulmonary irritation and cough may develop after inhalation exposure. Pulmonary edema is rarely reported. Respiratory failure may develop secondary to CNS depression in severe exposures. Goodpasture's syndrome has been associated with one case of occupational exposure.
    3.6.2) CLINICAL EFFECTS
    A) DYSPNEA
    1) WITH POISONING/EXPOSURE
    a) Cough, chest discomfort and dyspnea may develop after inhalation (Snyder et al, 1992; Buie et al, 1986; Nager & O'Connor, 1998) and after ingestion (Chang et al, 1999).
    B) ACUTE LUNG INJURY
    1) WITH POISONING/EXPOSURE
    a) Prolonged exposure can result in shortness of breath, painful cough, and possibly pulmonary edema (ILO, 1998).
    b) Acute lung injury (pulmonary edema) has been reported after severe inhalation exposure and has been found at autopsy (Buie et al, 1986; Winek et al, 1981; Snyder et al, 1992; Manno et al, 1992; Leikin et al, 1990; Tay et al, 1995). However, it is not common (US DHHS, 1990).
    c) CASE SERIES - After ingestion, 1 of 6 patients developed pulmonary edema (Chang et al, 1999).
    C) APNEA
    1) WITH POISONING/EXPOSURE
    a) Respiratory failure may develop secondary to CNS depression in severe exposures (Manno et al, 1990; (Chang et al, 1999).
    b) CASE REPORT - Sudden death occurred to a 27-year-old male following inhalation of a paint stripping agent containing 77% methylene chloride, which was being used in a poorly ventilated area. The main autopsy findings showed bilateral pulmonary congestion and edema, petechiae in the lungs, and portal inflammation of the liver. Methylene chloride levels in the blood and pulmonary exudate were 140 and 540 mg/L, respectively. The combination of the autopsy findings and the lab analysis of the biological fluids established the cause of death as asphyxia secondary to inhalation of fumes from a cleaning agent containing methylene chloride (Zarrabeitia et al, 2001).
    c) CASE REPORT - A 22-year-old male died while removing lacquer, in a poorly ventilated area, using a solvent containing 84% methylene chloride. An autopsy showed facial erythema, petechial bleeding of the ocular conjunctiva and visceral pleura, acute dilatation of the right heart ventricle, and pulmonary and cerebral edema. Methylene chloride levels in the blood of the left and right heart ventricles and in pulmonary tissue were 5420 mcg/mL, 4590 mcg/mL, and 7280 mcg/mL, respectively. It is believed that death occurred due to asphyxiation following inhalation of excessive amounts of methylene chloride fumes in a poorly ventilated workplace (Fechner et al, 2001).
    D) ACUTE RESPIRATORY INSUFFICIENCY
    1) Respiratory depression is a result of severe, prolonged exposure. Death from respiratory insufficiency has occurred after exposure to methylene chloride (Lewis, 1998).
    E) LUNG FINDING
    1) WITH POISONING/EXPOSURE
    a) Absorption occurs easily through the lungs (Raffle et al, 1994). Physical exertion increases absorption of methylene chloride, as well as its conversion to carbon monoxide with subsequent elevation of the carboxyhemoglobin levels (Harbison, 1998).

Neurologic

    3.7.1) SUMMARY
    A) WITH POISONING/EXPOSURE
    1) Headache and light-headedness are common after inhalation. Psychomotor performance is impaired with acute exposure. Syncope, CNS depression and coma may develop with more severe exposure. CNS excitation including seizures may also occur.
    3.7.2) CLINICAL EFFECTS
    A) CENTRAL NERVOUS SYSTEM FINDING
    1) WITH POISONING/EXPOSURE
    a) Exposure to methylene chloride may cause a number of neurologic symptoms, including headache, giddiness, light-headedness, dizziness, euphoria, irritability, loss of appetite, sleepiness, weakness, fatigue, stupor, convulsions, numbness, anesthesia and limb dysesthesias (ILO, 1998; ACGIH, 1991; Baselt, 1997; Budavari, 1996). The central nervous system depressant effects have reportedly produced fatalities (Baselt, 1997).
    b) CASE REPORT: A 45-year-old man developed nausea and vomiting, and lost consciousness after using a commercial solvent containing methylene chloride for stripping wall paint. Following oxygen therapy, he regained consciousness, and presented to the ED with drowsiness, headache, neck pain, and numbness in the right thumb and index finger. An ECG, chest x-ray, and all laboratory results were normal; however, his carboxyhemoglobin (COHb) level was 8.7% (normal, less than 5% in nonsmokers), which increased to 17.3% the following day. Non-contrast computed axial tomographic scan of the head showed subtle bilateral hypodensities in globus pallidus. Following supportive care, including 2 sessions of hyperbaric oxygen therapy (46 minutes each at 2.8 atmospheres) on day 1 and 2, his condition improved gradually (Cabrera et al, 2011).
    c) Headaches, dizziness, nausea, and throat irritation were reported in 11 soldiers following inhalational exposure to a paint stripping agent containing methylene chloride (dichloromethane) while working in a small closed room. All 11 soldiers recovered with supportive therapy (Jacubovich et al, 2005).
    d) COMBINATION INGESTION - A man developed altered mental status and toxic hepatitis after ingesting approximately half of the content of a 250-mL bottle of chloroform and dichloromethane. Following supportive care, he gradually recovered and was discharged 2 weeks after ingestion (Kim, 2008).
    e) COMBINATION EXPOSURE: A 37-year-old chemist with a 5-year history of headaches, dizziness, and fatigue due to a long-term inhalational exposure to dichloromethane and iodomethane, presented with ataxia, increasing inhibition, dizziness, dysarthria, and a confusional and delirious state a day after distilling dichloromethane and iodomethane at work. His symptoms deteriorated in the next several hours and his lethargy progressed to stupor and shallow coma, with episodes of confusion, restlessness, and aggression. All laboratory tests and a CT scan were normal. An MRI scan of the brain revealed the presence of a T2-hyperintense lesion in the splenium of the corpus callosum, suggestive of myelinolysis. His symptoms gradually improved and a repeat MRI of the brain 16 days later revealed complete resolution of all lesions in the corpus callosum as well as in the cerebellar hemispheres (Ehler et al, 2011).
    B) SEIZURE
    1) Seizures have been reported after severe acute and chronic exposure (Tariot, 1983; Hall & Rumack, 1990; Lewis, 1996; Chang et al, 1999).
    C) COMA
    1) WITH POISONING/EXPOSURE
    a) Coma has been reported (Ehler et al, 2011).
    b) High concentrations of methylene chloride produce an anesthetic effect that ranges from fatigue to light-headedness, drowsiness and unconsciousness; there is a narrow margin of safety between mild and severe effects (ILO, 1998).
    c) Methylene chloride is a general anesthetic. All phases of anesthesia may develop after exposure, beginning with excitation up to and including coma and death (Leikin et al, 1990; Hall & Rumack, 1990) Rioux & Myers; 1989; (Budavari, 1996). Generally methylene chloride induced CNS depression is reversible. Victims typically regain consciousness within several hours, except in cases of hypoxic encephalopathy (Chang et al, 1999).
    d) CASE SERIES: Chang et al (1999) reported on six patients who ingested methylene chloride. All six developed some degree of CNS depression, ranging from somnolence and weakness to deep coma.
    D) HEADACHE
    1) WITH POISONING/EXPOSURE
    a) Acute inhalation of methylene chloride vapors commonly produces dizziness, headache and drowsiness (Cabrera et al, 2011; Ehler et al, 2011) (Rioux & Myers, 1988) (Leikin et al, 1990; Rudge, 1990; Hall & Rumack, 1990). These and other CNS effects are generally transient, resolving after exposure has ceased (Lash et al, 1991).
    1) Neurologic effects are produced by methylene chloride's direct solvent effect and production of carbon monoxide. Initial symptoms following acute high-level exposure are probably related to direct effects rather than carbon monoxide production (Mahmud & Kales, 1999).
    b) CASE REPORT - A 26-year-old male reported headaches after repeated workplace exposure to methylene chloride (Mahmud & Kales, 1999).
    c) CASE SERIES - Mild light-headedness that resolved within 5 minutes of exposure occurred in three persons exposed for 1 hour to concentrations of 868 to 1,000 ppm (Stewart et al, 1972).
    d) CASE SERIES - Forty-six workers exposed to methylene chloride (75 to 100 ppm) reported significantly more neurological complaints (e.g., headache, dizziness, incoordination) than did 12 unexposed workers. Persistent CNS effects were not clinically measurable in a follow-up of 29 of the exposed workers (Cherry et al, 1981).
    e) CASE SERIES - No statistically significant increase in complaints of dizziness or recurring severe headaches were reported in a group of 150 workers chronically exposed for 10 or more years to methylene chloride (average 475 ppm 8 hr Time Weighted Average), as compared to unexposed workers (Soden, 1993).
    E) ATAXIA
    1) WITH POISONING/EXPOSURE
    a) Ataxia may occur with exposure (Ehler et al, 2011).
    F) HEARING LOSS
    1) WITH POISONING/EXPOSURE
    a) ALTERED HEARING/VISION/SMELL - Short-term (e.g. 3 to 4 hours) inhalation of vapors equal to or in excess of 300 ppm may cause temporarily decreased hearing and vision (US DHHS, 1993).
    1) CASE SERIES - No statistically significant decrement in color vision or sense of smell was reported in a cohort study of 25 retired workers previously exposed for more than 23 years to methylene chloride (Lash et al, 1991).
    G) TOXIC ENCEPHALOPATHY
    1) WITH POISONING/EXPOSURE
    a) ORGANIC BRAIN SYNDROME has been reported following occupational exposure.
    1) CASE REPORT - Memory loss, ataxia, intellectual impairment and dysarthria associated with bilateral temporal lobe degeneration developed in a middle aged man after three years of occupational exposure to 300 to 1,000 ppm methylene chloride. It was postulated that chronic carbon monoxide poisoning from methylene chloride metabolism was responsible (Barrowcliff & Knell, 1979).
    2) CASE REPORT - Sporadic complaints of flashbacks, left-side paresthesias, shortness of breath, and nausea were reported in a 52-year-old woman painting her house with methylene chloride-containing spray paint. The flashbacks consisted of vivid recollections of childhood memories. Symptoms stopped after paint use was terminated (Nager & O'Connor, 1998).
    3) CASE SERIES - No statistically significant excess complaints of memory loss were reported by 150 workers chronically exposed for 10 or more years to methylene chloride (average 475 ppm 8 hr Time Weighted Average), as compared to unexposed workers (Soden, 1993).
    4) CASE SERIES - No statistically significant decrements in memory or psychomotor response were reported in a study of 25 retired airline mechanics previously exposed an average of 23.8 years to methylene chloride, as compared to unexposed workers. Exposed workers scored lower on attention tests and higher in memory tests than unexposed persons, but these effects were not statistically significant (Lash et al, 1991).
    5) CASE SERIES - No statistically significant EEG changes were identified in 29 workers exposed to methylene chloride vapors ranging from 75 to 100 ppm (Cherry et al, 1981).
    H) BEHAVIOR SHOWING REDUCED MOTOR ACTIVITY
    1) WITH POISONING/EXPOSURE
    a) PSYCHOMOTOR SLOWING has been reported following acute exposures.
    1) Reduced motor speed and prolonged simple and complex reaction times develop after 4 hours of exposure to 800 ppm (Winneke, 1981; Winneke, 1982).
    2) CASE SERIES - No persistent, statistically significant deficits in psychomotor performance were determined in 25 retired airline mechanics previously exposed an average of 23.8 years to methylene chloride (Lash et al, 1991).
    3) CASE SERIES - No statistically significant effects on motor nerve conduction velocities were identified in 29 workers chronically exposed to methylene chloride vapors ranging from 75 to 100 ppm (Cherry et al, 1981).
    I) PARESTHESIA
    1) WITH POISONING/EXPOSURE
    a) Paresthesias of the extremities as well as neurasthenic disorders are symptoms of methylene chloride exposure (ACGIH, 1991; ITI, 1995).
    b) CASE SERIES - No statistically significant excess reports of paresthesias were reported in 150 workers chronically exposed for 10 or more years to methylene chloride (average 475 ppm 8 hr Time Weighted Average), as compared to unexposed workers (Soden, 1993).
    c) CASE REPORT - Left-sided paresthesias were reported in a 52-year-old female following inhalation of a spray paint containing methylene chloride (Nager & O'Connor, 1998).
    J) NEUROPATHY
    1) WITH POISONING/EXPOSURE
    a) CASE SERIES - No significantly abnormal EEGs, motor nerve conduction velocities and psychological test results were identified in 29 workers chronically exposed to methylene chloride vapors ranging from 75 to 100 ppm (Cherry et al, 1981).
    b) CASE SERIES - No statistically significant abnormalities in physiological (e.g., smell, color vision, grip strength, evoked response) and psychological functions (e.g. task performance, memory, attention, spatial ability) were reported in a study of 25 retired airline mechanics previously exposed for an average of 23.8 years to methylene chloride vapors (82 to 826 ppm), as compared to 21 retired unexposed workers (Lash et al, 1991).
    K) FACIAL PALSY
    1) WITH POISONING/EXPOSURE
    a) A 21-year-old soldier reported headache, dizziness, and nausea 2 hours after 3 hours of exposure, in a small closed room, to a paint stripping agent containing methylene chloride (dichloromethane). Ten other soldiers also reported headache, dizziness, and throat irritation following exposure to the paint stripping agent. Following supportive care, the 21-year-old soldier's symptoms resolved. The next morning, the patient presented with peripheral facial nerve palsy with weakness and asymmetry of the left side of his face. Laboratory data revealed normal kidney and liver function, O2 saturation of 98%, and serial blood carboxyhemoglobin levels of 0.3% to 0.4%. His facial palsy resolved following supportive therapy. The ten other soldiers exposed to the paint stripping agent did not report the development of peripheral facial palsy. It is unclear whether methylene chloride was the causative agent, however due to the patient's lack of other medical risk factors and the temporal association with methylene chloride exposure, a causal relationship cannot be ruled out (Jacubovich et al, 2005).

Gastrointestinal

    3.8.1) SUMMARY
    A) WITH POISONING/EXPOSURE
    1) Nausea and vomiting are common after inhalation exposure. Gastrointestinal ulceration and bleeding and pancreatitis have been reported after ingestion.
    3.8.2) CLINICAL EFFECTS
    A) NAUSEA AND VOMITING
    1) WITH POISONING/EXPOSURE
    a) Nausea and vomiting are common after inhalation exposure (Cabrera et al, 2011; Jacubovich et al, 2005; ITI, 1995; Rudge, 1990; Rioux & Myers, 1989; Nager & O'Connor, 1998) and ingestion (Chang et al, 1999). Loss of appetite is due to CNS depression(ILO, 1998).
    B) GASTRIC ULCER WITH HEMORRHAGE
    1) WITH POISONING/EXPOSURE
    a) Ingestion of methylene chloride has caused death from gastrointestinal hemorrhage (Morgan, 1993).
    b) CASE REPORT - Duodenal and jejunal ulcers with associated hemorrhage developed in a 38-year-old man after ingesting one to two pints of a methylene-chloride- based paint remover. Six months later diverticula developed in the areas of ulceration (Hughes et al, 1976).
    c) CASE SERIES - Corrosive gastrointestinal injury was reported in two of six patients with methylene chloride ingestion. Two of three patients undergoing panendoscopic examination showed corrosive GI injury patterns. All of the patients reported GI symptoms (Chang et al, 1999).
    C) PANCREATITIS
    1) WITH POISONING/EXPOSURE
    a) CASE SERIES - Pancreatitis was reported in one of six patients after methylene chloride ingestion (Chang et al, 1999). The exact mechanism is unknown, but may be either a direct effect of the toxin or a result of pancreatic hypoperfusion.

Hepatic

    3.9.1) SUMMARY
    A) WITH POISONING/EXPOSURE
    1) Elevated liver enzyme levels rarely occur.
    3.9.2) CLINICAL EFFECTS
    A) LIVER ENZYMES ABNORMAL
    1) WITH POISONING/EXPOSURE
    a) One case of hepatitis and several cases of elevated hepatic enzymes have been reported, but significant hepatotoxicity is unlikely with exposures that are within the current occupational exposure limits (US DHHS, 1990).
    1) COMBINATION INGESTION - A 23-year-old man presented with altered mental status 30 minutes after ingesting approximately half of the content of a 250-mL bottle of chloroform and dichloromethane. On day 2, laboratory results revealed elevated liver enzymes which reached peak levels on postingestion day 5. His blood carboxyhemoglobin concentration was 8.9% (Ref range, nonsmokers 0% to 1.9%; smokers, 1.9% to 4.9%). He experienced jaundice, nausea, vomiting, abdominal pain, and general weakness 3 days postingestion. Abdominal CT revealed severe fatty infiltration of the liver parenchyma. Following supportive care, he gradually recovered and was discharged 2 weeks after ingestion. His liver enzymes levels returned to almost the reference range 4 weeks later (Kim, 2008).
    a) It is suggested that the mechanism of hepatic injury is induced by toxic metabolites by 2 hepatic pathways, cytochrome P450-dependent metabolism and glutathione S-transferase (GST)-dependent. Phosgene, a main hepatotoxic metabolite, and hydrochloric acid are produced from chloroform by the oxidative cytochrome P-450 pathway. In addition, this pathway produces carbon monoxide and carbon dioxide (via formyl chloride) from dichloromethane. The glutathione pathway produces a glutathione conjugate and formaldehyde and subsequently carbon dioxide (Kim, 2008).
    2) CASE REPORT - Elevations in hepatic enzymes have been reported after dermal exposure and inhalation, and may be delayed for several days (Miller et al, 1985; Puurunen & Sotaniemi, 1985; Cordes et al, 1988; Leikin et al, 1990).
    3) CASE SERIES - There were no statistically significant differences in serum levels of hepatic enzymes (AST; ALT) between unexposed workers and 90 workers chronically exposed for 10 or more years to methylene chloride vapors averaging 475 ppm as an 8 hours Time Weighted Average (Soden, 1993).
    4) CASE SERIES - Elevated liver enzyme levels were reported in two of six patients after methylene chloride ingestion (Chang et al, 1999). The authors speculate that the increased liver enzyme levels may be due to either a direct effect of methylene chloride or as a result of hepatic hypoperfusion.
    B) LIVER DAMAGE
    1) WITH POISONING/EXPOSURE
    a) Liver disease has been reported after occupational exposure to methylene chloride (ACGIH, 1991). Ingestion has resulted in severe liver damage (Morgan, 1993).
    3.9.3) ANIMAL EFFECTS
    A) ANIMAL STUDIES
    1) HEPATOCELLULAR DAMAGE
    a) For rats, the liver is a primary target organ; increased hepatocellular vacuolization and increased multinuclear hepatocytes have been reported after exposure to methylene chloride by inhalation or by ingestion via drinking water (ACGIH, 1991).

Genitourinary

    3.10.1) SUMMARY
    A) WITH POISONING/EXPOSURE
    1) Renal effects are rare. Hematuria, acute tubular necrosis and the development of Goodpasture's syndrome have been associated with exposure to methylene chloride.
    3.10.2) CLINICAL EFFECTS
    A) BLOOD IN URINE
    1) WITH POISONING/EXPOSURE
    a) Ingestion of methylene chloride has caused renal injury (Morgan, 1993). Hematuria is unusual but has been reported after ingestion and inhalation (Keogh et al, 1984; Miller et al, 1985) Hughes et al, 1976; (Chang et al, 1999).
    B) CRUSH SYNDROME
    1) WITH POISONING/EXPOSURE
    a) CASE REPORT: Hematuria and acute tubular necrosis developed in a 19-year-old male after working with methylene chloride based tile remover in a poorly ventilated room (Miller et al, 1985).
    b) CASE SERIES: Acute tubular necrosis was reported in two of six patients after methylene chloride ingestion (Chang et al, 1999). The authors speculate that the necrosis may be related to either a direct effect of methylene chloride or to renal hypoperfusion.
    C) GLOMERULONEPHRITIS
    1) WITH POISONING/EXPOSURE
    a) CASE REPORT: A 16-year-old woman developed Goodpasture's syndrome associated with occupational exposure to hydrocarbon fumes, including methylene chloride and trichloroethane(Keogh et al, 1984).

Hematologic

    3.13.1) SUMMARY
    A) WITH POISONING/EXPOSURE
    1) Methylene chloride is metabolized to carbon monoxide. Carboxyhemoglobin as high as 50% are reported, and levels may continue to rise for several hours after exposure has ceased. The apparent half-life of carboxyhemoglobin is prolonged to 13 hours because of ongoing production of carboxyhemoglobin.
    3.13.2) CLINICAL EFFECTS
    A) CARBOXYHEMOGLOBINEMIA
    1) WITH POISONING/EXPOSURE
    a) The toxic effects of methylene chloride exposure are related in part to its conversion to carbon monoxide, which yields increased concentrations of carboxyhemoglobin in the blood (Cabrera et al, 2011; Morgan, 1993; Baselt, 1997). In general, the concentrations are usually not high enough to produce symptoms of carbon monoxide poisoning (Morgan, 1993), however there is a report of a carboxyhemoglobin level of 35% in a patient who subsequently developed persistent hypotension and hypoxemia, became comatose, and died approximately 9 days after intentionally ingesting 300 mL of methylene chloride (Chang et al, 1999).
    b) The increase in carboxyhemoglobin is directly proportional to the magnitude of the vapor exposure. Significant amounts of carbon monoxide and carboxyhemoglobin were produced in humans exposed to 500 to 1,000 ppm methylene chloride (ACGIH, 1991).
    c) CASE REPORT: A 24-year-old man was found unconscious 6.5 hours after applying one gallon of paint stripper (containing 70% to 85% dichloromethane, methanol, isopropyl alcohol, 2-butoxyethanol, and ethanol) to the floor of a baptismal font in a church. He did not respond to resuscitative efforts and was pronounced dead. During an autopsy, cardiomegaly with 4-chamber dilatation and coronary atherosclerosis with 50% occlusion of the left anterior descending artery were observed. Postmortem laboratory results showed a COHb of 10% and a blood dichloromethane concentration of 37.8 mg/dL. It was determined that dichloromethane poisoning, resulting in hypoxia and dysrhythmias, was the cause of death (Macisaac et al, 2013).
    d) CASE REPORT: A 65-year-old man was found unconscious 2.5 hours after entering an empty paint-mixing tank and using a chemical paint stripper containing 60% to 100% dichloromethane, 10% to 30% methanol, and 1% to 5% Stoddard solvent. Another worker, a 45-year-old man, entered the tank to rescue him, but he also lost consciousness. Both men were removed from the tank an hour later, but the first man did not respond to resuscitative efforts and was pronounced dead. Postmortem laboratory results showed a COHb concentration below the limit of detection (less than 5%) and a blood dichloromethane concentration of 220 mg/dL. On presentation, the second patient had a pulse rate of 100 beats/min, a blood pressure of 118/68 mmHg, and he was combative with a GCS 1-4-1. Laboratory analysis showed a respiratory acidosis (pH of 7.32, pCO2 51 mmHg), a COHb concentration of 4%, an osmol gap of 17 mOsm/kg (normal less than 10 mOsm/kg), and serum methanol concentration of 15.1 mg/dL (normal less than 1.5). Following supportive care, his mental status improved after 4 hours and he was extubated. His COHb concentrations continued to increase for the first 24 hours to a peak concentration of 10.2%, but returned to normal after about 60 hours and he was discharged on day 4 (Macisaac et al, 2013).
    e) CASE REPORT: A 23-year-old man developed altered mental status and toxic hepatitis after ingesting approximately half of the content of a 250-mL bottle of chloroform and dichloromethane. His blood carboxyhemoglobin concentration was 8.9% (Ref range, nonsmokers 0% to 1.9%; smokers, 1.9% to 4.9%). Following supportive care, he gradually recovered and was discharged 2 weeks after ingestion (Kim, 2008).
    f) CASE REPORT: Carboxyhemoglobin levels up to 12.1% developed in an adult female after ingestion of an estimated 300 mL of a product (Nitromors) that contained methylene chloride, methanol, cellulose acetate, triethanolamine, paraffin wax and detergents (Hughes & Tracey, 1993).
    g) CASE SERIES: In a study of volunteers exposed to 200 ppm for 7.5-hour work days, the maximum carboxyhemoglobin concentration was 6.8% (DiVincenzo & Kaplan, 1981).
    h) CASE SERIES: A one- to two-hour exposure of 11 nonsmokers to 500 to 1,000 ppm produced increased carboxyhemoglobin levels of up to 15%. Carboxyhemoglobin was increased for 17 to 24 hours in some individuals (Stewart et al, 1972).
    i) CASE REPORT: Occupational exposure to methylene chloride resulted in dose-related increases in carboxyhemoglobin (Ott et al, 1983).
    j) CASE REPORT (ADULT) - Carboxyhemoglobin concentrations of 26% and 40% were reported after the use of methylene-chloride-containing paint removers (Langehennig et al, 1976).
    k) CASE SERIES: Chang et al (1999) documented carboxyhemoglobin levels of 35% and 8.4%, respectively, in 2 patients after ingestion of methylene chloride.
    l) CASE SERIES - Carboxyhemoglobin levels of 12% to 20.4% were reported in 4 patients exposed to a personal defense spray containing 49% methylene chloride and 0.8% CS after the contents were discharged into a closed space. Associated symptoms included headache, dizziness, and nausea. All recovered uneventfully after treatment with 100% normobaric oxygen (Duenas et al, 2000).
    m) Carboxyhemoglobin concentrations as high as 50% have been reported (Fagin et al, 1980; Langehennig et al, 1976).
    n) Smokers who are exposed to methylene chloride concentrations of 500 ppm or greater have had carboxyhemoglobin levels of 15% or greater (US DHHS, 1990).
    B) ANEMIA
    1) Anemia may develop after chronic exposure to methylene chloride (ITI, 1995). Decreased erythrocyte and hemoglobin levels have been reported (ILO, 1998).
    C) LACK OF EFFECT
    1) CASE SERIES - There were no significant differences in the hemoglobin levels of methylene chloride-exposed workers (10 or more years, average 475 ppm 8 hr Time Weighted Average) as compared to unexposed workers (Soden, 1993).
    3.13.3) ANIMAL EFFECTS
    A) ANIMAL STUDIES
    1) CARBOXYHEMOGLOBINEMIA
    a) In rats and mice exposed to methylene chloride at 200, 500, or 1000 ppm for 12-hour periods, the conversion to carboxyhemoglobin was saturable and no greater than after 8 hours of exposure (Kim & Carlson, 1986).

Dermatologic

    3.14.1) SUMMARY
    A) WITH POISONING/EXPOSURE
    1) Skin irritation, pain, numbness and mild burns may develop with acute exposure. Severe burns may develop with prolonged exposure or immersion. Systemic effects can result from absorption through the skin.
    3.14.2) CLINICAL EFFECTS
    A) SKIN IRRITATION
    1) WITH POISONING/EXPOSURE
    a) Contact with liquid methylene chloride produces pain, skin irritation, and burns if the liquid is not removed (ACGIH, 1991). Immersion can result in pain and numbness (Harbison, 1998).
    b) Extreme dryness and fissuring may occur due to the 'degreasing' action of the solvent (Harbison, 1998). Methylene chloride is mildly irritating to skin with repeated contact. This problem is accentuated if the chemical is 'sealed' to skin by shoes or tight clothing, and is most severe with paint remover formulations that form a 'skin' or film (Clayton & Clayton, 1994).
    B) DERMATITIS
    1) WITH POISONING/EXPOSURE
    a) Dry scaly dermatitis is an effect of exposure to methylene chloride (Lewis, 1998).
    C) CHEMICAL BURN
    1) WITH POISONING/EXPOSURE
    a) Skin irritation and burns are an effect of exposure to methylene chloride (ITI, 1998). Severe chemical burns have been reported with prolonged skin contact or immersion (Raffle et al, 1994; Hall & Rumack, 1990; Tay et al, 1995).
    D) POISONING
    1) WITH POISONING/EXPOSURE
    a) Although methylene chloride can be absorbed through the skin sufficiently to cause systemic symptoms, chlorinated hydrocarbons are considered to be poorly absorbed through the skin (Zenz, 1994; Harbison, 1998).

Reproductive

    3.20.1) SUMMARY
    A) Methylene chloride was not found to be teratogenic in mice and rabbits. It crosses the placenta, and is found in breast milk, and has been associated with increased spontaneous abortion. However, few reproductive effects are seen in rats.
    3.20.2) TERATOGENICITY
    A) HUMANS
    1) Some central nervous system defects were reported in the offspring of women exposed to methylene chloride and other solvents (Holmberg & Nurminen, 1980; Holmberg, 1979; Kurppa, 1983).
    2) Some women exposed to environmental methylene chloride in nearby factory emissions had lower infant birthweights than infants born to unexposed mothers (Bell et al, 1991).
    B) LACK OF EFFECT
    1) There is limited evidence that methylene chloride is not teratogenic at exposures to sub-toxic doses in laboratory animals; it was not teratogenic in the mouse or rabbit (Clayton & Clayton, 1994; Schardein, 1993).
    C) ANIMAL STUDIES
    1) Methylene chloride administered at a dose of 1,250 ppm to pregnant rats and mice from day 6 to day 15 of gestation produced developmental abnormalities of the musculoskeletal systems in the offspring. In the rats, some fetal urogenital systems were also developmentally affected (RTECS , 2000).
    2) Methylene chloride did not cause structural malformations in rats exposed to an airborne concentration of 4,500 ppm, but did produce lower birth weights (Hardin & Manson, 1980).
    3) Some offspring of maternally exposed rats lagged in behavioral development and did not adapt well to new situations (Bornschein, 1980; RTECS , 2000).
    4) When given orally to rats at a dose of 0.1 mL, methylene chloride produced teratogenic effects (Nehez, 1983). Alternatively, in mice, oral doses of 4 percent in the diet produced maternal toxicity, although no teratogenic effects were seen (Nishio, 1984).
    5) In some studies, methylene chloride was not found to be teratogenic in some laboratory animals after exposures to sub-toxic doses; no adverse reproductive effects were seen in the mouse or rabbit (Clayton & Clayton, 1994; Schardein, 1993). Additionally, no teratogenic effects were found in rats after exposure to as much as 1,500 ppm for 2 years (Clayton & Clayton, 1994).
    6) Methylene chloride was not teratogenic in Sprague-Dawley rats by the oral or inhalation routes, at doses up to 2.4 mmol/kg/day or 300 ppm for 6 hours/day from day 6 to day 20 of gestation, respectively (Payan et al, 1995).
    3.20.3) EFFECTS IN PREGNANCY
    A) ABORTION
    1) Increased spontaneous abortion has been reported with occupation exposure to methylene chloride (Schardein, 1993). Two occupational studies found slight increases in spontaneous abortion rates in women exposed to methylene chloride during the first trimester of pregnancy (Axelsson et al, 1984) Taskinen et al, 1986).
    B) PLACENTAL BARRIER
    1) After maternal exposure, methylene chloride crosses the placenta and is found in embryonic tissue (ILO, 1998; AMA, 1985).
    C) ANIMAL STUDIES
    1) Experimental animal studies indicate that methylene chloride can cross the placenta. Methylene chloride was found in rat fetuses when the mothers were exposed to airborne levels as low as 100 ppm (Withey & Karpinski, 1985).
    2) When given to pregnant rats, methylene chloride was more concentrated in the maternal blood than in the fetus (Anders & Sunram, 1982). 14C-Methylene chloride was transferred to the fetuses at levels slightly lower than those found in maternal plasma (Payan et al, 1995).
    3) Groups of rats and mice exposed to 1,250 ppm dichloromethane by inhalation for 7 hours/day on days 6 to 15 of pregnancy demonstrated no effects on the average number of implantation sites per litter, litter size, incidence of fetal reabsorptions, fetal sex ratios or fetal body measurements (HSDB , 2000).
    3.20.4) EFFECTS DURING BREAST-FEEDING
    A) BREAST MILK
    1) Methylene chloride has been found in breast milk of occupationally exposed women (AMA, 1985; ILO, 1998).

Carcinogenicity

    3.21.1) IARC CATEGORY
    A) IARC Carcinogenicity Ratings for CAS75-09-2 (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):
    1) IARC Classification
    a) Listed as: Dichloromethane (methylene chloride)
    b) Carcinogen Rating: 2A
    1) The agent (mixture) is probably carcinogenic to humans. The exposure circumstance entails exposures that are probably carcinogenic to humans. This category is used when there is limited evidence of carcinogenicity in humans and sufficient evidence of carcinogenicity in experimental animals. In some cases, an agent (mixture) may be classified in this category when there is inadequate evidence of carcinogenicity in humans and sufficient evidence of carcinogenicity in experimental animals and strong evidence that the carcinogenesis is mediated by a mechanism that also operates in humans. Exceptionally, an agent, mixture or exposure circumstance may be classified in this category solely on the basis of limited evidence of carcinogenicity in humans.
    3.21.2) SUMMARY/HUMAN
    A) Methylene chloride has been classified as probably carcinogenic to humans (Group 2A) by IARC following a systematic review and evaluation.
    3.21.3) HUMAN STUDIES
    A) CARCINOMA
    1) The International Agency for Research on Cancer (IARC) has determined that methylene chloride is probably carcinogenic to humans (Group 2A) after a systematic review and evaluation of the scientific evidence by leading independent experts (International Agency for Research on Cancer, 2015).
    2) Methylene chloride is listed as a potential occupational carcinogen by NIOSH (2000), and is classified as A3 (confirmed animal carcinogen with unknown relevance to humans) by the American Conference of Governmental Industrial Hygienists ((IARC, 2000)), and as B2 (probable human carcinogen) by the IRIS system (IRIS , 2000).
    3) Of seven cohort studies, two found an excess of pancreatic cancer and three did not; one found an excess of liver and biliary tract cancer; one found an excess of prostate cancer; one found an excess of breast and gynecological cancer; and one found an increase in cervical cancer. All of these excesses were small ((IARC, 2000)).
    4) Case-control studies have found a risk of astrocytic brain tumors, female breast cancer, rectal cancer and possibly lung cancer after exposure to methylene chloride. There was not a sufficiently increased risk to suggest causality ((IARC, 2000)).
    5) The US National Toxicology Program considers methylene chloride an anticipated carcinogen, based on sufficient evidence of carcinogenicity (respiratory tract and liver neoplasms; mammary gland fibroadenoma) in rats exposed by inhalation (US DHHS, 1994).
    6) Human studies published in 1978 through 1989 were considered inadequate, but there has been sufficient evidence of carcinogenicity in laboratory animals (IRIS , 2000).
    7) A case-control study conducted in Montreal, Canada of occupational exposures to any of 6 chlorinated solvents (carbon tetrachloride, methylene chloride, 1,1,1-trichloroethane, chloroform, trichloroethylene, and tetrachloroethylene) and association with cancer found an increased risk of prostate cancer with tetrachloroethylene exposure and an increased risk of melanoma with trichloroethylene exposure. The analysis that included 3730 cancer cases (occurring from 1979 to 1985) and 533 population controls focused on the following 11 cancer types: esophagus, stomach, colon, rectum, liver, pancreas, prostate, bladder, kidney, melanoma, and non-Hodgkin lymphoma. An association was observed between tetrachloroethylene exposure and risk of prostate cancer (odds ratio [OR], 2.2; 95% CI, 0.8 to 5.7 for any exposure and OR, 4.3; 95% CI, 1.4 to 13 for substantial exposure), as well as between trichloroethylene exposure and melanoma risk (OR, 3; 95% CI, 1.2 to 7.2 for any exposure and OR, 3.2; 95% CI, 1 to 9.9 for substantial exposure). There was also an association between substantial exposure to chlorinated alkenes (ie, trichloroethylene and tetrachloroethylene) in general and melanoma risk (OR, 2.6; 95% CI, 1 to 7.1). Substantial exposure was defined as a degree of confidence that the exposure actually occurred of probable or definite, a medium or high solvent concentration and frequency of exposure, and a duration of exposure that was greater than 5 years. While an association between substantial exposure to chloroform and risk of pancreatic cancer exists (OR, 10.6; 95% CI, 1.2 to 93), this was based on only 2 exposed workers. The majority of ORs were close to null or like the chloroform and pancreatic association, were based on very small numbers, thereby providing limited power to detect real risk (Christensen et al, 2013).
    8) A proportionate mortality study found no increase in deaths from malignant neoplasms among workers exposed for up to 30 years to mean concentrations of methylene chloride ranging from 33 to 118.8 ppm compared to control populations (HSDB , 2000). Another study found no significant increases in the rate of death from any cause in exposed workers (Hearne & Pifer, 1999).
    9) A review of the cancer epidemiology of methylene chloride has concluded that there is no strong or consistent evidence for any type of cancer resulting from occupational exposure to methylene chloride. Reports of increased cancer of the pancreas, liver and biliary passages, brain and breast have been sporadic and weak (Dell et al, 1999).
    10) The US EPA classifies methylene chloride as B2, a "probable human carcinogen." This is based on inadequate human data and sufficient evidence of carcinogenicity in animals, including increased incidence of alveolar/bronchiolar neoplasms in male and female mice, and increased incidence of benign mammary tumors in both sexes of rats, salivary gland sarcomas in male rats and leukemia in female rats. This classification is supported by some positive genotoxicity data, although results in mammalian systems are generally negative (IRIS , 2000).
    11) Epidemiologic studies have not shown a definite association between cancer and methylene chloride; however, they lack sufficient statistical power to detect increases at potencies comparable to those seen in experimental animal studies (Von Burg, 1995).
    B) HEPATIC CARCINOMA
    1) Excess deaths (4 observed; 1.34 expected) were reported in cellulose fiber production workers exposed to methylene chloride. Excess deaths were identified in a follow-up study, but no new cancer deaths were reported (Lanes et al, 1993).
    2) Studies reviewed by the IRIS system (2000) were not sufficient to clearly implicate methylene chloride as a cause of pancreatic tumors. One study suggested possible increased liver and biliary tract cancers.
    3) Analysis of results from a study of Kodak Company workers, adjusting for the healthy worker effect and length of follow-up failed to find an excess risk of liver cancer (Stayner & Bailer, 1993).
    4) No deaths due to hepatic cancer (1964 to 1988) were identified in a cohort study of 1,013 Eastman Kodak Company workers exposed to methylene chloride. Death due to pancreatic cancer did not seem to be related to occupational methylene chloride exposure (Hearne et al, 1990).
    5) In a follow-up mortality study through 1994 on two international cohorts totalling 2,324 men, no significant excesses were seen for any cause of death, including cancers. These two groups were exposed to an average of 39 ppm methylene chloride for 17 years, or to 26 ppm for 24 years (Hearne & Pifer, 1999).
    C) PULMONARY CARCINOMA
    1) Analysis of results from a study of Eastman Kodak Company workers, adjusting for the healthy worker effect and length of follow-up failed to find an excess risk of lung cancer (Stayner & Bailer, 1993).
    2) No significant excess deaths due to lung cancer (1964 to 1988) were identified in a cohort study of 1,013 Eastman Kodak Company workers exposed to methylene chloride (Hearne et al, 1990).
    D) BRAIN CARCINOMA
    1) An association between "likely" occupational exposure to methylene chloride and astrocytic brain cancer was reported in a case-control study involving white males (Heineman et al, 1994).
    E) BREAST CARCINOMA
    1) A retrospective analysis of mortality records, with exposure estimated from occupation and industry codes, found a possible association between methylene chloride exposure and breast cancer (Cantor et al, 1995). Because of limitations of the study, these results need to be confirmed by additional research.
    F) PROSTATE CARCINOMA
    1) In a study of cellulose-fiber production workers exposed to methylene chloride, men employed for 20 years or more had an increased mortality from prostate cancer. In the high exposure group (350 to 700 ppm) there were 13 observed deaths vs 7.26 expected; in the low exposure group (50 to 100 ppm) there were 9 deaths vs 6.41 expected (Gibbs et al, 1996).
    G) CERVICAL CARCINOMA
    1) In a study of cellulose-fiber production workers exposed to methylene chloride, women employed for 20 years or more had an increased mortality from cervical cancer. In the low exposure group (50 to 100 ppm) there were 5 deaths vs 1.69 expected; in the high exposure group (350 to 700 ppm) there were no excess deaths from cervical cancer (Gibbs et al, 1996).
    H) RISK FACTORS
    1) An excess risk of cancer from inhalation was predicted based on estimated air concentrations of methylene chloride with typical use (without adequate ventilation) and application of an exposure factor and the US EPA inhalation unit risk for methylene chloride (Skoglund & Roy, 1995). This study was theoretical, without direct measurement of human exposure and cancer incidence.
    2) A physiologically-based pharmacokinetic model of cancer risk assessment for methylene chloride concluded that the risk to humans from a lifetime exposure was only 3.7 x 10(-8), a figure two orders of magnitude lower than that obtained from the US EPA's linearized multistage model (Andersen & Krishnan, 1994).
    3.21.4) ANIMAL STUDIES
    A) CARCINOMA
    1) Divergent results have been obtained in rodent studies (Clayton & Clayton, 1994; ACGIH, 1991).
    2) A 2-year study of exposure to 3,500 ppm by inhalation for 6 hours/day, 5 days/week, resulted in no increased oncogenesis in hamsters and statistically significant salivary tumors in male rats and benign mammary tumors in male and female rats.
    3) Mice exposed to 4,000 ppm for 2 years had increased lung and liver tumors.
    4) A 2-year study of exposure to 3,500 ppm methylene chloride by inhalation (6 hours/day, 5 days/week), resulted in statistically significant endocrine tumors such as salivary gland sarcomas in male rats and benign mammary tumor growth in male and female rats (p 5; HSDB , 2000; RTECS , 2000). In contrast, some rodent studies have yielded divergent results (Clayton & Clayton, 1994; ACGIH, 1991); hamsters exposed to the same concentrations of methylene chloride had no observed increase in oncogenesis and lacked evidence of definite target organ toxicity (Burek, 1984; HSDB , 2000).
    5) Mice exposed to 2,000 ppm methylene chloride by inhalation for 2 years, 5 hours/day, were reported to have developed thoracic, lung and other respiratory tract tumors (RTECS , 2000; HSDB , 2000)
    6) In a study in which over 1,400 female B6C3F1 mice were exposed to 2,000 ppm of methylene chloride for 6 hours/day for varying durations, an exposure period of 26 weeks was sufficient to induce pulmonary tumors, while the incidence of liver neoplasms depended on total duration of exposure. A longer post-exposure period showed an increase in the number of lung, but not liver tumors, detected in mice (Kari et al, 1993). No specific oncogene activation was seen for either tumor type (Maronpot et al, 1995).

Genotoxicity

    A) Results concerning the genotoxicity of methylene chloride have been conflicting in vivo and in vitro. It is generally mutagenic and can cause DNA breaks and chromosomal aberrations.

Monitoring Parameters Levels

    4.1.1) SUMMARY
    A) Monitor vital signs and mental status.
    B) Order carboxyhemoglobin levels.
    C) Routine lab studies include: serum electrolytes, renal function, liver enzymes and lipase. Obtain arterial blood gases when significant pulmonary toxicity is observed.
    D) Dichloromethane concentrations are not rapidly available or useful to guide therapy.
    4.1.2) SERUM/BLOOD
    A) BLOOD/SERUM CHEMISTRY
    1) Liver enzyme levels and renal function tests should be monitored.
    B) HEMATOLOGIC
    1) The concentration of carboxyhemoglobin in blood may be proportional to the exposure concentration and duration (Shusterman et al, 1990). However, these results may be confounded by carbon monoxide from other sources (such as smoking) (Zenz, 1994).
    2) Methylene chloride may be measured in blood and breath; these plateau after 2 hours of exposure and decrease quickly after exposure ends (Baselt, 1997). The breath analysis has limited usefulness (Clayton & Clayton, 1994).

Radiographic Studies

    A) RADIOGRAPHIC-OTHER
    1) Methylene chloride was radio-opaque in vitro (Dally et al, 1987).

Methods

    A) CHROMATOGRAPHY
    1) Expired air can be collected in a Saran bag and analyzed by Infrared or gas chromatography to establish the diagnosis and estimate the magnitude of the exposure. Methylene chloride can also be detected in blood and urine.

Life Support

    A) Support respiratory and cardiovascular function.

Patient Disposition

    6.3.1) DISPOSITION/ORAL EXPOSURE
    6.3.1.1) ADMISSION CRITERIA/ORAL
    A) A patient with signs of CNS toxicity, significant gastrointestinal symptoms, mucous membrane irritation, and any patient with an intentional exposure should be admitted.
    6.3.1.2) HOME CRITERIA/ORAL
    A) Asymptomatic adults and children can be kept home after inadvertent dermal or inhalation exposure or taste ingestions with dichloromethane household products. Any patient with a significant industrial exposure or an intentional ingestion should be admitted.
    6.3.1.3) CONSULT CRITERIA/ORAL
    A) Consult a poison center or medical toxicologist for assistance in managing patients with severe toxicity (ie, CNS depression, organ failure, significant CO poisoning), or in whom the diagnosis is unclear.

Monitoring

    A) Monitor vital signs and mental status.
    B) Order carboxyhemoglobin levels.
    C) Routine lab studies include: serum electrolytes, renal function, liver enzymes and lipase. Obtain arterial blood gases when significant pulmonary toxicity is observed.
    D) Dichloromethane concentrations are not rapidly available or useful to guide therapy.

Oral Exposure

    6.5.1) PREVENTION OF ABSORPTION/PREHOSPITAL
    A) EMESIS/NOT RECOMMENDED
    1) Emesis is not recommended because of the potential for CNS depression and seizures.
    B) ACTIVATED CHARCOAL/NOT RECOMMENDED
    1) Activated charcoal is not recommended because of limited efficacy, rapid absorption of dichloromethane after ingestion, and the risk of corrosive injury to the gastrointestinal tract.
    6.5.2) PREVENTION OF ABSORPTION
    A) EMESIS/NOT RECOMMENDED
    1) Emesis is NOT recommended because of the potential for CNS depression and seizures.
    B) ACTIVATED CHARCOAL/NOT RECOMMENDED
    1) Activated charcoal is not recommended because of limited efficacy, rapid absorption of dichloromethane after ingestion, and the risk of corrosive injury to the gastrointestinal tract.
    C) NASOGASTRIC TUBE
    1) Consider insertion of a soft, flexible nasogastric tube for gastric aspiration in patients with recent very large ingestions. The potential benefits must be weighed against the risk of further damaging burned gastrointestinal mucosa.
    6.5.3) TREATMENT
    A) SUPPORT
    1) Treatment is symptomatic and supportive. Remove contaminated clothing, wash exposed skin with soap and water.
    B) MONITORING OF PATIENT
    1) Monitor vital signs and mental status.
    2) Order carboxyhemoglobin levels.
    3) Routine lab studies include: serum electrolytes, renal function, liver enzymes and lipase. Obtain arterial blood gases when significant pulmonary toxicity is observed.
    4) Dichloromethane concentrations are not rapidly available or useful to guide therapy.
    C) OXYGEN
    1) Administer 100% oxygen to patients with symptoms of CO poisoning (headache, nausea, vomiting), a history of loss of consciousness, alterations in mental status or neurologic deficits. Continue as indicated by clinical status and carboxyhemoglobin levels.
    2) Because of apparent prolonged elimination of carboxyhemoglobin formed as the result of methylene chloride metabolism, prolonged treatment may be required (Mahmud & Kales, 1999; Chang et al, 1999).
    D) HYPERBARIC OXYGEN THERAPY
    1) Two patients who used a methylene chloride (25%) paint, sprayed in a semi-enclosed area, developed coma and peak carboxyhemoglobin concentrations of 11.5% and 13%. Psychometric testing showed severe dysfunction in both, which improved after hyperbaric oxygen therapy. Repeated 'dives' were administered 9 days later in the patient with the highest concentration because of persistence of cognitive dysfunction. The carboxyhemoglobin half-life in these 2 patients was shorter (4.75 and 6.5 hours) than that reported in untreated patients in one study (13 hours) (Rioux & Myers, 1989).
    2) (Rioux & Myers, 1989), but comparable to that reported after 100 percent normobaric oxygen in another (5.8 hours) (Sturmann et al, 1985).
    3) CASE REPORT: A 45-year-old man developed nausea and vomiting, and lost consciousness after using a commercial solvent containing methylene chloride for stripping wall paint. Following oxygen therapy, he regained consciousness, and presented to the ED with drowsiness, headache, neck pain, and numbness in the right thumb and index finger. An ECG, chest x-ray, and all laboratory results were normal; however, his carboxyhemoglobin (COHb) level was 8.7% (normal, less than 5% in nonsmokers), which increased to 17.3% the following day. Non-contrast computed axial tomographic scan of the head showed subtle bilateral hypodensities in globus pallidus. Following supportive care, including 2 sessions of hyperbaric oxygen therapy (46 minutes each at 2.8 atmospheres) on day 1 and 2, his condition improved gradually (Cabrera et al, 2011).
    4) The comparative efficacy of 100% normobaric oxygen versus hyperbaric oxygen (HBO) has not been studied in animals or humans with methylene chloride poisoning.
    5) Acute methylene chloride poisoning may cause neurological symptoms similar to acute carbon monoxide poisoning. Early alterations in consciousness are most likely due to a direct solvent effect and/or hypoxia. Neurological symptoms observed greater than one hour postexposure with an elevated carboxyhemoglobin level can be attributed to carbon monoxide intoxication. Patients with elevated carboxyhemoglobin levels and those with a history of loss of consciousness may be at risk for the delayed effects of carbon monoxide poisoning. Also, patients with persistent symptoms should be considered for hyperbaric oxygen therapy (Tomaszewski & Thom, 1994).
    E) ETHANOL
    1) CASE REPORT: A 51-year-old alcoholic man was treated with ethanol (target concentration range of 22 to 44 mmol/L) after developing confusion, new onset seizures, coma, metabolic acidosis, increased carboxyhemoglobin (COHb) concentration, and an acute abdomen after ingesting an unknown quantity of home-distilled alcohol (grappa), containing methylene chloride and methanol. Although ethanol was used to treat the concomitant methanol poisoning, it also decreased the production of COHb. Ethanol therapy was discontinued on day 2 with a COHb concentration of less than 5, the COHb concentration then rose to above 15%, and declined again when the ethanol was resumed 12 hours later. It was suggested that ethanol inhibits cytochrome P450 2E1, and competitively inhibits the metabolism of methylene chloride and the production of its metabolites. The patient was also treated with high flux renal replacement therapy and calcium folinate. Following further supportive care, his condition improved gradually; however, he remained on hemodialysis for a month after ICU discharge (Vetro et al, 2012).
    F) SEIZURE
    1) SUMMARY
    a) Attempt initial control with a benzodiazepine (eg, diazepam, lorazepam). If seizures persist or recur, administer phenobarbital or propofol.
    b) Monitor for respiratory depression, hypotension, and dysrhythmias. Endotracheal intubation should be performed in patients with persistent seizures.
    c) Evaluate for hypoxia, electrolyte disturbances, and hypoglycemia (or, if immediate bedside glucose testing is not available, treat with intravenous dextrose).
    2) DIAZEPAM
    a) ADULT DOSE: Initially 5 to 10 mg IV, OR 0.15 mg/kg IV up to 10 mg per dose up to a rate of 5 mg/minute; may be repeated every 5 to 20 minutes as needed (Brophy et al, 2012; Prod Info diazepam IM, IV injection, 2008; Manno, 2003).
    b) PEDIATRIC DOSE: 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 (Loddenkemper & Goodkin, 2011; Hegenbarth & American Academy of Pediatrics Committee on Drugs, 2008).
    c) Monitor for hypotension, respiratory depression, and the need for endotracheal intubation. Consider a second agent if seizures persist or recur after repeated doses of diazepam .
    3) NO INTRAVENOUS ACCESS
    a) DIAZEPAM may be given rectally or intramuscularly (Manno, 2003). RECTAL DOSE: CHILD: Greater than 12 years: 0.2 mg/kg; 6 to 11 years: 0.3 mg/kg; 2 to 5 years: 0.5 mg/kg (Brophy et al, 2012).
    b) MIDAZOLAM has been used intramuscularly and intranasally, particularly in children when intravenous access has not been established. ADULT DOSE: 0.2 mg/kg IM, up to a maximum dose of 10 mg (Brophy et al, 2012). PEDIATRIC DOSE: INTRAMUSCULAR: 0.2 mg/kg IM, up to a maximum dose of 7 mg (Chamberlain et al, 1997) OR 10 mg IM (weight greater than 40 kg); 5 mg IM (weight 13 to 40 kg); INTRANASAL: 0.2 to 0.5 mg/kg up to a maximum of 10 mg/dose (Loddenkemper & Goodkin, 2011; Brophy et al, 2012). BUCCAL midazolam, 10 mg, has been used in adolescents and older children (5-years-old or more) to control seizures when intravenous access was not established (Scott et al, 1999).
    4) LORAZEPAM
    a) MAXIMUM RATE: The rate of intravenous administration of lorazepam should not exceed 2 mg/min (Brophy et al, 2012; Prod Info lorazepam IM, IV injection, 2008).
    b) ADULT DOSE: 2 to 4 mg IV initially; repeat every 5 to 10 minutes as needed, if seizures persist (Manno, 2003; Brophy et al, 2012).
    c) PEDIATRIC DOSE: 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 (Brophy et al, 2012; Loddenkemper & Goodkin, 2011; Hegenbarth & American Academy of Pediatrics Committee on Drugs, 2008; Sreenath et al, 2009; Chin et al, 2008).
    5) PHENOBARBITAL
    a) ADULT LOADING DOSE: 20 mg/kg IV at an infusion rate of 50 to 100 mg/minute IV. An additional 5 to 10 mg/kg dose may be given 10 minutes after loading infusion if seizures persist or recur (Brophy et al, 2012).
    b) Patients receiving high doses will require endotracheal intubation and may require vasopressor support (Brophy et al, 2012).
    c) PEDIATRIC LOADING DOSE: 20 mg/kg may be given as single or divided application (2 mg/kg/minute in children weighing less than 40 kg up to 100 mg/min in children weighing greater than 40 kg). A plasma concentration of about 20 mg/L will be achieved by this dose (Loddenkemper & Goodkin, 2011).
    d) REPEAT PEDIATRIC DOSE: Repeat doses of 5 to 20 mg/kg may be given every 15 to 20 minutes if seizures persist, with cardiorespiratory monitoring (Loddenkemper & Goodkin, 2011).
    e) MONITOR: For hypotension, respiratory depression, and the need for endotracheal intubation (Loddenkemper & Goodkin, 2011; Manno, 2003).
    f) SERUM CONCENTRATION MONITORING: Monitor serum concentrations over the next 12 to 24 hours. Therapeutic serum concentrations of phenobarbital range from 10 to 40 mcg/mL, although the optimal plasma concentration for some individuals may vary outside this range (Hvidberg & Dam, 1976; Choonara & Rane, 1990; AMA Department of Drugs, 1992).
    6) OTHER AGENTS
    a) If seizures persist after phenobarbital, propofol or pentobarbital infusion, or neuromuscular paralysis with general anesthesia (isoflurane) and continuous EEG monitoring should be considered (Manno, 2003). Other anticonvulsants can be considered (eg, valproate sodium, levetiracetam, lacosamide, topiramate) if seizures persist or recur; however, there is very little data regarding their use in toxin induced seizures, controlled trials are not available to define the optimal dosage ranges for these agents in status epilepticus (Brophy et al, 2012):
    1) VALPROATE SODIUM: ADULT DOSE: An initial dose of 20 to 40 mg/kg IV, at a rate of 3 to 6 mg/kg/minute; may give an additional dose of 20 mg/kg 10 minutes after loading infusion. PEDIATRIC DOSE: 1.5 to 3 mg/kg/minute (Brophy et al, 2012).
    2) LEVETIRACETAM: ADULT DOSE: 1000 to 3000 mg IV, at a rate of 2 to 5 mg/kg/min IV. PEDIATRIC DOSE: 20 to 60 mg/kg IV (Brophy et al, 2012; Loddenkemper & Goodkin, 2011).
    3) LACOSAMIDE: ADULT DOSE: 200 to 400 mg IV; 200 mg IV over 15 minutes (Brophy et al, 2012). PEDIATRIC DOSE: In one study, median starting doses of 1.3 mg/kg/day and maintenance doses of 4.7 mg/kg/day were used in children 8 years and older (Loddenkemper & Goodkin, 2011).
    4) TOPIRAMATE: ADULT DOSE: 200 to 400 mg nasogastric/orally OR 300 to 1600 mg/day orally divided in 2 to 4 times daily (Brophy et al, 2012).
    G) HYPOTENSIVE EPISODE
    1) SUMMARY
    a) Infuse 10 to 20 milliliters/kilogram of isotonic fluid and keep the patient supine. If hypotension persists, administer dopamine or norepinephrine. Consider central venous pressure monitoring to guide further fluid therapy.
    2) DOPAMINE
    a) DOSE: Begin at 5 micrograms per kilogram per minute progressing in 5 micrograms per kilogram per minute increments as needed (Prod Info dopamine hcl, 5% dextrose IV injection, 2004). If hypotension persists, dopamine may need to be discontinued and a more potent vasoconstrictor (eg, norepinephrine) should be considered (Prod Info dopamine hcl, 5% dextrose IV injection, 2004).
    b) CAUTION: If ventricular dysrhythmias occur, decrease rate of administration (Prod Info dopamine hcl, 5% dextrose IV injection, 2004). Extravasation may cause local tissue necrosis, administration through a central venous catheter is preferred (Prod Info dopamine hcl, 5% dextrose IV injection, 2004).
    3) NOREPINEPHRINE
    a) PREPARATION: 4 milligrams (1 amp) added to 1000 milliliters of diluent provides a concentration of 4 micrograms/milliliter of norepinephrine base. Norepinephrine bitartrate should be mixed in dextrose solutions (dextrose 5% in water, dextrose 5% in saline) since dextrose-containing solutions protect against excessive oxidation and subsequent potency loss. Administration in saline alone is not recommended (Prod Info norepinephrine bitartrate injection, 2005).
    b) DOSE
    1) ADULT: Dose range: 0.1 to 0.5 microgram/kilogram/minute (eg, 70 kg adult 7 to 35 mcg/min); titrate to maintain adequate blood pressure (Peberdy et al, 2010).
    2) CHILD: Dose range: 0.1 to 2 micrograms/kilogram/minute; titrate to maintain adequate blood pressure (Kleinman et al, 2010).
    3) CAUTION: Extravasation may cause local tissue ischemia, administration by central venous catheter is advised (Peberdy et al, 2010).
    H) HYPERTENSIVE EPISODE
    1) Monitor vital signs regularly. For mild/moderate hypertension without evidence of end organ damage, pharmacologic intervention is generally not necessary. Sedative agents such as benzodiazepines may be helpful in treating hypertension and tachycardia in agitated patients, especially if a sympathomimetic agent is involved in the poisoning.
    2) For hypertensive emergencies (severe hypertension with evidence of end organ injury (CNS, cardiac, renal), or emergent need to lower mean arterial pressure 20% to 25% within one hour), sodium nitroprusside is preferred. Nitroglycerin and phentolamine are possible alternatives.
    3) SODIUM NITROPRUSSIDE/INDICATIONS
    a) Useful for emergent treatment of severe hypertension secondary to poisonings. Sodium nitroprusside has a rapid onset of action, a short duration of action and a half-life of about 2 minutes (Prod Info NITROPRESS(R) injection for IV infusion, 2007) that can allow accurate titration of blood pressure, as the hypertensive effects of drug overdoses are often short lived.
    4) SODIUM NITROPRUSSIDE/DOSE
    a) ADULT: Begin intravenous infusion at 0.1 microgram/kilogram/minute and titrate to desired effect; up to 10 micrograms/kilogram/minute may be required (American Heart Association, 2005). Frequent hemodynamic monitoring and administration by an infusion pump that ensures a precise flow rate is mandatory (Prod Info NITROPRESS(R) injection for IV infusion, 2007). PEDIATRIC: Initial: 0.5 to 1 microgram/kilogram/minute; titrate to effect up to 8 micrograms/kilogram/minute (Kleinman et al, 2010).
    5) SODIUM NITROPRUSSIDE/SOLUTION PREPARATION
    a) The reconstituted 50 mg solution must be further diluted in 250 to 1000 mL D5W to desired concentration (recommended 50 to 200 mcg/mL) (Prod Info NITROPRESS(R) injection, 2004). Prepare fresh every 24 hours; wrap in aluminum foil. Discard discolored solution (Prod Info NITROPRESS(R) injection for IV infusion, 2007).
    6) SODIUM NITROPRUSSIDE/MAJOR ADVERSE REACTIONS
    a) Severe hypotension; headaches, nausea, vomiting, abdominal cramps; thiocyanate or cyanide toxicity (generally from prolonged, high dose infusion); methemoglobinemia; lactic acidosis; chest pain or dysrhythmias (high doses) (Prod Info NITROPRESS(R) injection for IV infusion, 2007). The addition of 1 gram of sodium thiosulfate to each 100 milligrams of sodium nitroprusside for infusion may help to prevent cyanide toxicity in patients receiving prolonged or high dose infusions (Prod Info NITROPRESS(R) injection for IV infusion, 2007).
    7) SODIUM NITROPRUSSIDE/MONITORING PARAMETERS
    a) Monitor blood pressure every 30 to 60 seconds at onset of infusion; once stabilized, monitor every 5 minutes. Continuous blood pressure monitoring with an intra-arterial catheter is advised (Prod Info NITROPRESS(R) injection for IV infusion, 2007).
    8) NITROGLYCERIN/INDICATIONS
    a) May be used to control hypertension, and is particularly useful in patients with acute coronary syndromes or acute pulmonary edema (Rhoney & Peacock, 2009).
    9) NITROGLYCERIN/ADULT DOSE
    a) Begin infusion at 10 to 20 mcg/min and increase by 5 or 10 mcg/min every 5 to 10 minutes until the desired hemodynamic response is achieved (American Heart Association, 2005). Maximum rate 200 mcg/min (Rhoney & Peacock, 2009).
    10) NITROGLYCERIN/PEDIATRIC DOSE
    a) Usual Dose: 29 days or Older: 1 to 5 mcg/kg/min continuous IV infusion. Maximum 60 mcg/kg/min (Laitinen et al, 1997; Nam et al, 1989; Rasch & Lancaster, 1987; Ilbawi et al, 1985; Friedman & George, 1985).
    I) ACUTE LUNG INJURY
    1) ONSET: Onset of acute lung injury after toxic exposure may be delayed up to 24 to 72 hours after exposure in some cases.
    2) NON-PHARMACOLOGIC TREATMENT: The treatment of acute lung injury is primarily supportive (Cataletto, 2012). Maintain adequate ventilation and oxygenation with frequent monitoring of arterial blood gases and/or pulse oximetry. If a high FIO2 is required to maintain adequate oxygenation, mechanical ventilation and positive-end-expiratory pressure (PEEP) may be required; ventilation with small tidal volumes (6 mL/kg) is preferred if ARDS develops (Haas, 2011; Stolbach & Hoffman, 2011).
    a) To minimize barotrauma and other complications, use the lowest amount of PEEP possible while maintaining adequate oxygenation. Use of smaller tidal volumes (6 mL/kg) and lower plateau pressures (30 cm water or less) has been associated with decreased mortality and more rapid weaning from mechanical ventilation in patients with ARDS (Brower et al, 2000). More treatment information may be obtained from ARDS Clinical Network website, NIH NHLBI ARDS Clinical Network Mechanical Ventilation Protocol Summary, http://www.ardsnet.org/node/77791 (NHLBI ARDS Network, 2008)
    3) FLUIDS: Crystalloid solutions must be administered judiciously. Pulmonary artery monitoring may help. In general the pulmonary artery wedge pressure should be kept relatively low while still maintaining adequate cardiac output, blood pressure and urine output (Stolbach & Hoffman, 2011).
    4) ANTIBIOTICS: Indicated only when there is evidence of infection (Artigas et al, 1998).
    5) EXPERIMENTAL THERAPY: Partial liquid ventilation has shown promise in preliminary studies (Kollef & Schuster, 1995).
    6) CALFACTANT: In a multicenter, randomized, blinded trial, endotracheal instillation of 2 doses of 80 mL/m(2) calfactant (35 mg/mL of phospholipid suspension in saline) in infants, children, and adolescents with acute lung injury resulted in acute improvement in oxygenation and lower mortality; however, no significant decrease in the course of respiratory failure measured by duration of ventilator therapy, intensive care unit, or hospital stay was noted. Adverse effects (transient hypoxia and hypotension) were more frequent in calfactant patients, but these effects were mild and did not require withdrawal from the study (Wilson et al, 2005).
    7) However, in a multicenter, randomized, controlled, and masked trial, endotracheal instillation of up to 3 doses of calfactant (30 mg) in adults only with acute lung injury/ARDS due to direct lung injury was not associated with improved oxygenation and longer term benefits compared to the placebo group. It was also associated with significant increases in hypoxia and hypotension (Willson et al, 2015).
    J) CORTICOSTEROID
    1) Administration of steroids has not been shown to provide any significant change in the course of methylene chloride poisoning.

Inhalation Exposure

    6.7.1) DECONTAMINATION
    A) Move patient from the toxic environment to fresh air. Monitor for respiratory distress. If cough or difficulty in breathing develops, evaluate for hypoxia, respiratory tract irritation, bronchitis, or pneumonitis.
    B) OBSERVATION: Carefully observe patients with inhalation exposure for the development of any systemic signs or symptoms and administer symptomatic treatment as necessary.
    C) INITIAL TREATMENT: Administer 100% humidified supplemental oxygen, perform endotracheal intubation and provide assisted ventilation as required. Administer inhaled beta-2 adrenergic agonists, if bronchospasm develops. Consider systemic corticosteroids in patients with significant bronchospasm (National Heart,Lung,and Blood Institute, 2007). Exposed skin and eyes should be flushed with copious amounts of water.
    6.7.2) TREATMENT
    A) OXYGEN
    1) Administer 100% oxygen to patients with symptoms of CO poisoning (headache, nausea, vomiting), a history of loss of consciousness, alterations in mental status or neurologic deficits. Continue as indicated by clinical status and carboxyhemoglobin levels.
    2) Because of apparent prolonged elimination of carboxyhemoglobin formed as the result of methylene chloride metabolism, prolonged treatment may be required (Mahmud & Kales, 1999; Chang et al, 1999).
    B) HYPERBARIC OXYGEN THERAPY
    1) Two patients who used a methylene chloride (25%) paint, sprayed in a semi-enclosed area, developed coma and peak carboxyhemoglobin concentrations of 11.5% and 13%. Psychometric testing showed severe dysfunction in both, which improved after hyperbaric oxygen therapy. Repeated 'dives' were administered 9 days later in the patient with the highest concentration because of persistence of cognitive dysfunction (Rioux & Myers, 1989).
    2) The carboxyhemoglobin half-life in these 2 patients was shorter (4.75 and 6.5 hours) than that reported in untreated patients (13 hours) (Ratney et al, 1974), but comparable to that reported after 100% normobaric oxygen (5.8 hours) (Sturmann et al, 1985).
    3) The comparative efficacy of 100% normobaric oxygen versus hyperbaric oxygen (HBO) has not been studied in animals or humans with methylene chloride poisoning.
    4) Acute methylene chloride poisoning may cause neurological symptoms similar to acute carbon monoxide poisoning. Early alterations in consciousness are most likely due to a direct solvent effect and/or hypoxia. Neurological symptoms observed greater than one hour postexposure with an elevated carboxyhemoglobin level can be attributed to carbon monoxide intoxication. Patients with elevated carboxyhemoglobin levels and those with a history of loss of consciousness may be at risk for the delayed effects of carbon monoxide. Also, patients with persistent symptoms should be considered for hyperbaric oxygen therapy (Tomaszewski & Thom, 1994).
    C) SEIZURE
    1) SUMMARY
    a) Attempt initial control with a benzodiazepine (eg, diazepam, lorazepam). If seizures persist or recur, administer phenobarbital or propofol.
    b) Monitor for respiratory depression, hypotension, and dysrhythmias. Endotracheal intubation should be performed in patients with persistent seizures.
    c) Evaluate for hypoxia, electrolyte disturbances, and hypoglycemia (or, if immediate bedside glucose testing is not available, treat with intravenous dextrose).
    2) DIAZEPAM
    a) ADULT DOSE: Initially 5 to 10 mg IV, OR 0.15 mg/kg IV up to 10 mg per dose up to a rate of 5 mg/minute; may be repeated every 5 to 20 minutes as needed (Brophy et al, 2012; Prod Info diazepam IM, IV injection, 2008; Manno, 2003).
    b) PEDIATRIC DOSE: 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 (Loddenkemper & Goodkin, 2011; Hegenbarth & American Academy of Pediatrics Committee on Drugs, 2008).
    c) Monitor for hypotension, respiratory depression, and the need for endotracheal intubation. Consider a second agent if seizures persist or recur after repeated doses of diazepam .
    3) NO INTRAVENOUS ACCESS
    a) DIAZEPAM may be given rectally or intramuscularly (Manno, 2003). RECTAL DOSE: CHILD: Greater than 12 years: 0.2 mg/kg; 6 to 11 years: 0.3 mg/kg; 2 to 5 years: 0.5 mg/kg (Brophy et al, 2012).
    b) MIDAZOLAM has been used intramuscularly and intranasally, particularly in children when intravenous access has not been established. ADULT DOSE: 0.2 mg/kg IM, up to a maximum dose of 10 mg (Brophy et al, 2012). PEDIATRIC DOSE: INTRAMUSCULAR: 0.2 mg/kg IM, up to a maximum dose of 7 mg (Chamberlain et al, 1997) OR 10 mg IM (weight greater than 40 kg); 5 mg IM (weight 13 to 40 kg); INTRANASAL: 0.2 to 0.5 mg/kg up to a maximum of 10 mg/dose (Loddenkemper & Goodkin, 2011; Brophy et al, 2012). BUCCAL midazolam, 10 mg, has been used in adolescents and older children (5-years-old or more) to control seizures when intravenous access was not established (Scott et al, 1999).
    4) LORAZEPAM
    a) MAXIMUM RATE: The rate of intravenous administration of lorazepam should not exceed 2 mg/min (Brophy et al, 2012; Prod Info lorazepam IM, IV injection, 2008).
    b) ADULT DOSE: 2 to 4 mg IV initially; repeat every 5 to 10 minutes as needed, if seizures persist (Manno, 2003; Brophy et al, 2012).
    c) PEDIATRIC DOSE: 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 (Brophy et al, 2012; Loddenkemper & Goodkin, 2011; Hegenbarth & American Academy of Pediatrics Committee on Drugs, 2008; Sreenath et al, 2009; Chin et al, 2008).
    5) PHENOBARBITAL
    a) ADULT LOADING DOSE: 20 mg/kg IV at an infusion rate of 50 to 100 mg/minute IV. An additional 5 to 10 mg/kg dose may be given 10 minutes after loading infusion if seizures persist or recur (Brophy et al, 2012).
    b) Patients receiving high doses will require endotracheal intubation and may require vasopressor support (Brophy et al, 2012).
    c) PEDIATRIC LOADING DOSE: 20 mg/kg may be given as single or divided application (2 mg/kg/minute in children weighing less than 40 kg up to 100 mg/min in children weighing greater than 40 kg). A plasma concentration of about 20 mg/L will be achieved by this dose (Loddenkemper & Goodkin, 2011).
    d) REPEAT PEDIATRIC DOSE: Repeat doses of 5 to 20 mg/kg may be given every 15 to 20 minutes if seizures persist, with cardiorespiratory monitoring (Loddenkemper & Goodkin, 2011).
    e) MONITOR: For hypotension, respiratory depression, and the need for endotracheal intubation (Loddenkemper & Goodkin, 2011; Manno, 2003).
    f) SERUM CONCENTRATION MONITORING: Monitor serum concentrations over the next 12 to 24 hours. Therapeutic serum concentrations of phenobarbital range from 10 to 40 mcg/mL, although the optimal plasma concentration for some individuals may vary outside this range (Hvidberg & Dam, 1976; Choonara & Rane, 1990; AMA Department of Drugs, 1992).
    6) OTHER AGENTS
    a) If seizures persist after phenobarbital, propofol or pentobarbital infusion, or neuromuscular paralysis with general anesthesia (isoflurane) and continuous EEG monitoring should be considered (Manno, 2003). Other anticonvulsants can be considered (eg, valproate sodium, levetiracetam, lacosamide, topiramate) if seizures persist or recur; however, there is very little data regarding their use in toxin induced seizures, controlled trials are not available to define the optimal dosage ranges for these agents in status epilepticus (Brophy et al, 2012):
    1) VALPROATE SODIUM: ADULT DOSE: An initial dose of 20 to 40 mg/kg IV, at a rate of 3 to 6 mg/kg/minute; may give an additional dose of 20 mg/kg 10 minutes after loading infusion. PEDIATRIC DOSE: 1.5 to 3 mg/kg/minute (Brophy et al, 2012).
    2) LEVETIRACETAM: ADULT DOSE: 1000 to 3000 mg IV, at a rate of 2 to 5 mg/kg/min IV. PEDIATRIC DOSE: 20 to 60 mg/kg IV (Brophy et al, 2012; Loddenkemper & Goodkin, 2011).
    3) LACOSAMIDE: ADULT DOSE: 200 to 400 mg IV; 200 mg IV over 15 minutes (Brophy et al, 2012). PEDIATRIC DOSE: In one study, median starting doses of 1.3 mg/kg/day and maintenance doses of 4.7 mg/kg/day were used in children 8 years and older (Loddenkemper & Goodkin, 2011).
    4) TOPIRAMATE: ADULT DOSE: 200 to 400 mg nasogastric/orally OR 300 to 1600 mg/day orally divided in 2 to 4 times daily (Brophy et al, 2012).
    D) HYPOTENSIVE EPISODE
    1) SUMMARY
    a) Infuse 10 to 20 milliliters/kilogram of isotonic fluid and keep the patient supine. If hypotension persists, administer dopamine or norepinephrine. Consider central venous pressure monitoring to guide further fluid therapy.
    2) DOPAMINE
    a) DOSE: Begin at 5 micrograms per kilogram per minute progressing in 5 micrograms per kilogram per minute increments as needed (Prod Info dopamine hcl, 5% dextrose IV injection, 2004). If hypotension persists, dopamine may need to be discontinued and a more potent vasoconstrictor (eg, norepinephrine) should be considered (Prod Info dopamine hcl, 5% dextrose IV injection, 2004).
    b) CAUTION: If ventricular dysrhythmias occur, decrease rate of administration (Prod Info dopamine hcl, 5% dextrose IV injection, 2004). Extravasation may cause local tissue necrosis, administration through a central venous catheter is preferred (Prod Info dopamine hcl, 5% dextrose IV injection, 2004).
    3) NOREPINEPHRINE
    a) PREPARATION: 4 milligrams (1 amp) added to 1000 milliliters of diluent provides a concentration of 4 micrograms/milliliter of norepinephrine base. Norepinephrine bitartrate should be mixed in dextrose solutions (dextrose 5% in water, dextrose 5% in saline) since dextrose-containing solutions protect against excessive oxidation and subsequent potency loss. Administration in saline alone is not recommended (Prod Info norepinephrine bitartrate injection, 2005).
    b) DOSE
    1) ADULT: Dose range: 0.1 to 0.5 microgram/kilogram/minute (eg, 70 kg adult 7 to 35 mcg/min); titrate to maintain adequate blood pressure (Peberdy et al, 2010).
    2) CHILD: Dose range: 0.1 to 2 micrograms/kilogram/minute; titrate to maintain adequate blood pressure (Kleinman et al, 2010).
    3) CAUTION: Extravasation may cause local tissue ischemia, administration by central venous catheter is advised (Peberdy et al, 2010).
    E) HYPERTENSIVE EPISODE
    1) Monitor vital signs regularly. For mild/moderate hypertension without evidence of end organ damage, pharmacologic intervention is generally not necessary. Sedative agents such as benzodiazepines may be helpful in treating hypertension and tachycardia in agitated patients, especially if a sympathomimetic agent is involved in the poisoning.
    2) For hypertensive emergencies (severe hypertension with evidence of end organ injury (CNS, cardiac, renal), or emergent need to lower mean arterial pressure 20% to 25% within one hour), sodium nitroprusside is preferred. Nitroglycerin and phentolamine are possible alternatives.
    3) SODIUM NITROPRUSSIDE/INDICATIONS
    a) Useful for emergent treatment of severe hypertension secondary to poisonings. Sodium nitroprusside has a rapid onset of action, a short duration of action and a half-life of about 2 minutes (Prod Info NITROPRESS(R) injection for IV infusion, 2007) that can allow accurate titration of blood pressure, as the hypertensive effects of drug overdoses are often short lived.
    4) SODIUM NITROPRUSSIDE/DOSE
    a) ADULT: Begin intravenous infusion at 0.1 microgram/kilogram/minute and titrate to desired effect; up to 10 micrograms/kilogram/minute may be required (American Heart Association, 2005). Frequent hemodynamic monitoring and administration by an infusion pump that ensures a precise flow rate is mandatory (Prod Info NITROPRESS(R) injection for IV infusion, 2007). PEDIATRIC: Initial: 0.5 to 1 microgram/kilogram/minute; titrate to effect up to 8 micrograms/kilogram/minute (Kleinman et al, 2010).
    5) SODIUM NITROPRUSSIDE/SOLUTION PREPARATION
    a) The reconstituted 50 mg solution must be further diluted in 250 to 1000 mL D5W to desired concentration (recommended 50 to 200 mcg/mL) (Prod Info NITROPRESS(R) injection, 2004). Prepare fresh every 24 hours; wrap in aluminum foil. Discard discolored solution (Prod Info NITROPRESS(R) injection for IV infusion, 2007).
    6) SODIUM NITROPRUSSIDE/MAJOR ADVERSE REACTIONS
    a) Severe hypotension; headaches, nausea, vomiting, abdominal cramps; thiocyanate or cyanide toxicity (generally from prolonged, high dose infusion); methemoglobinemia; lactic acidosis; chest pain or dysrhythmias (high doses) (Prod Info NITROPRESS(R) injection for IV infusion, 2007). The addition of 1 gram of sodium thiosulfate to each 100 milligrams of sodium nitroprusside for infusion may help to prevent cyanide toxicity in patients receiving prolonged or high dose infusions (Prod Info NITROPRESS(R) injection for IV infusion, 2007).
    7) SODIUM NITROPRUSSIDE/MONITORING PARAMETERS
    a) Monitor blood pressure every 30 to 60 seconds at onset of infusion; once stabilized, monitor every 5 minutes. Continuous blood pressure monitoring with an intra-arterial catheter is advised (Prod Info NITROPRESS(R) injection for IV infusion, 2007).
    8) NITROGLYCERIN/INDICATIONS
    a) May be used to control hypertension, and is particularly useful in patients with acute coronary syndromes or acute pulmonary edema (Rhoney & Peacock, 2009).
    9) NITROGLYCERIN/ADULT DOSE
    a) Begin infusion at 10 to 20 mcg/min and increase by 5 or 10 mcg/min every 5 to 10 minutes until the desired hemodynamic response is achieved (American Heart Association, 2005). Maximum rate 200 mcg/min (Rhoney & Peacock, 2009).
    10) NITROGLYCERIN/PEDIATRIC DOSE
    a) Usual Dose: 29 days or Older: 1 to 5 mcg/kg/min continuous IV infusion. Maximum 60 mcg/kg/min (Laitinen et al, 1997; Nam et al, 1989; Rasch & Lancaster, 1987; Ilbawi et al, 1985; Friedman & George, 1985).
    F) ACUTE LUNG INJURY
    1) ONSET: Onset of acute lung injury after toxic exposure may be delayed up to 24 to 72 hours after exposure in some cases.
    2) NON-PHARMACOLOGIC TREATMENT: The treatment of acute lung injury is primarily supportive (Cataletto, 2012). Maintain adequate ventilation and oxygenation with frequent monitoring of arterial blood gases and/or pulse oximetry. If a high FIO2 is required to maintain adequate oxygenation, mechanical ventilation and positive-end-expiratory pressure (PEEP) may be required; ventilation with small tidal volumes (6 mL/kg) is preferred if ARDS develops (Haas, 2011; Stolbach & Hoffman, 2011).
    a) To minimize barotrauma and other complications, use the lowest amount of PEEP possible while maintaining adequate oxygenation. Use of smaller tidal volumes (6 mL/kg) and lower plateau pressures (30 cm water or less) has been associated with decreased mortality and more rapid weaning from mechanical ventilation in patients with ARDS (Brower et al, 2000). More treatment information may be obtained from ARDS Clinical Network website, NIH NHLBI ARDS Clinical Network Mechanical Ventilation Protocol Summary, http://www.ardsnet.org/node/77791 (NHLBI ARDS Network, 2008)
    3) FLUIDS: Crystalloid solutions must be administered judiciously. Pulmonary artery monitoring may help. In general the pulmonary artery wedge pressure should be kept relatively low while still maintaining adequate cardiac output, blood pressure and urine output (Stolbach & Hoffman, 2011).
    4) ANTIBIOTICS: Indicated only when there is evidence of infection (Artigas et al, 1998).
    5) EXPERIMENTAL THERAPY: Partial liquid ventilation has shown promise in preliminary studies (Kollef & Schuster, 1995).
    6) CALFACTANT: In a multicenter, randomized, blinded trial, endotracheal instillation of 2 doses of 80 mL/m(2) calfactant (35 mg/mL of phospholipid suspension in saline) in infants, children, and adolescents with acute lung injury resulted in acute improvement in oxygenation and lower mortality; however, no significant decrease in the course of respiratory failure measured by duration of ventilator therapy, intensive care unit, or hospital stay was noted. Adverse effects (transient hypoxia and hypotension) were more frequent in calfactant patients, but these effects were mild and did not require withdrawal from the study (Wilson et al, 2005).
    7) However, in a multicenter, randomized, controlled, and masked trial, endotracheal instillation of up to 3 doses of calfactant (30 mg) in adults only with acute lung injury/ARDS due to direct lung injury was not associated with improved oxygenation and longer term benefits compared to the placebo group. It was also associated with significant increases in hypoxia and hypotension (Willson et al, 2015).
    G) CORTICOSTEROID
    1) Administration of steroids has not been shown to provide any significant change in the course of methylene chloride poisoning.
    H) Treatment should include recommendations listed in the ORAL EXPOSURE section when appropriate.

Eye Exposure

    6.8.1) DECONTAMINATION
    A) EYE IRRIGATION, ROUTINE: 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, an ophthalmologic examination should be performed (Peate, 2007; Naradzay & Barish, 2006).

Dermal Exposure

    6.9.1) DECONTAMINATION
    A) DERMAL DECONTAMINATION
    1) DECONTAMINATION: Remove contaminated clothing and wash exposed area thoroughly with soap and water for 10 to 15 minutes. A physician may need to examine the area if irritation or pain persists (Burgess et al, 1999).

Summary

    A) TOXICITY: Inhalation is the usual route of occupational exposure. OSHA's short-term exposure limit: 125 ppm; 8-hour permissible exposure limit: 25 ppm; NIOSH immediately dangerous to life and health concentration: 2300 ppm. For humans, 50,000 ppm is considered life-threatening. The lowest oral dose reported to cause death is 357 mg/kg.
    B) Patients usually develop toxicity after ingestions of more than 25 mL of dichloromethane.
    C) Methylene chloride is metabolized to carbon monoxide, resulting in carboxyhemoglobin in the blood and toxic effects. When heated to decomposition, methylene chloride releases toxic phosgene, hydrogen chloride gas, and chlorine gas.

Minimum Lethal Exposure

    A) ADULT
    1) Methylene chloride is moderately toxic by ingestion, subcutaneous, and intraperitoneal routes, and mildly toxic by inhalation. Most occupational exposures are by inhalation; concentrations in excess of 50,000 ppm are thought to be immediately life-threatening (Hathaway et al, 1996; Lewis, 2000).
    2) OSHA's short-term exposure limit: 125 ppm; 8-hour permissible exposure limit: 25 ppm; NIOSH immediately dangerous to life and health lconcentration: 2300 ppm (Centers for Disease Control and Prevention (CDC), 2012).
    3) A 52-year-old man was found dead after using 6 ounces of a product containing 60% to 100% methylene chloride to strip a tub in an unventilated bathroom that was 5 feet by 8 feet by 8 feet (Centers for Disease Control and Prevention (CDC), 2012).
    4) An LDLo (lowest dose reported to cause death) of 357 mg/kg (oral) has been reported for humans (Lewis, 2000).
    5) The toxic effects of methylene chloride exposure are related in part to its conversion to carbon monoxide, which yields increased concentrations of carboxyhemoglobin in the blood (Morgan, 1993; Baselt, 1997). The phosgene released when methylene chloride is oxidized by an open flame also produces toxic effects (Baselt, 1997).

Maximum Tolerated Exposure

    A) ADULT
    1) In human experiments, inhalation of 500 to 1000 ppm for 1 or 2 hours produced lightheadedness; there was sustained elevation of carboxyhemoglobin levels in each of 11 nonsmoking subjects (Hathaway et al, 1996).
    2) No effects were seen in volunteers exposed to 250 ppm for up to 7.5 hours/day, 5 days/week for 2 weeks, or when male subjects were exposed to 500 ppm on 2 consecutive days. An excess in self-reported neurologic symptoms was found in workers repeatedly exposed to 75 to 100 ppm, although no significant deleterious effects were observed on clinical examination (ACGIH, 1991; Hathaway et al, 1996).
    3) Complaints of headache, fatigue, and irritation of the eyes and respiratory passages were reported by workers exposed to concentrations up to 5,000 ppm. Neurasthenic disorders were found in 50% and digestive disturbances in 30% of these workers (ACGIH, 1991).
    4) After one year of exposure, a chemist developed toxic encephalopathy with acoustical and optical delusions and hallucinations. Concentrations frequently exceeded 500 ppm of methylene chloride; levels of 660 ppm, 800 ppm and, near the floor, 3,600 ppm were noted (ACGIH, 1991; Hathaway et al, 1996).

Serum Plasma Blood Concentrations

    7.5.2) TOXIC CONCENTRATIONS
    A) TOXIC CONCENTRATION LEVELS
    1) ADULT
    a) The methylene chloride blood concentration in a 47-year-old male following a fatal inhalational exposure was 150 milligrams/liter (Goulle et al, 1999). In another fatal exposure, the methylene chloride concentration was 510 mg/L (Baselt, 1997).
    b) Blood levels should not exceed 1 mg/L methylene chloride in workers exposed to 100 ppm methylene chloride, and blood carboxyhemoglobin should not exceed 5 percent (Baselt, 1997).
    c) The post mortem methylene chloride blood concentration was 281 milligrams/liter in a worker who died after inhalation and dermal exposure to a paint stripper containing 75% methylene chloride, 8% methanol, 2% hydrofluoric acid and 3% o-dichlorobenzene while working in a tank. Autopsy revealed cerebral edema, mucosal hemorrhages in the larynx, hemorrhagic shock lung with congestion and pulmonary edema, fatty liver and partial thickness burns of 25% to 30% BSA (Tay et al, 1995).
    d) CASE REPORT: A 52-year-old man with a history of hyperlipidemia experienced a sudden cardiorespiratory arrest after refinishing a bathtub with an aircraft paint stripper (Tal-Strip II Aircraft coating remover) containing 60% to 100% methylene chloride. He was found unconscious in the bathroom and died at the hospital. Laboratory results revealed a blood methylene chloride concentration of 50 mg/L. An autopsy showed mild coronary atherosclerosis and mucus plugging of bronchi and bronchioles. It was estimated that 6 fluid ounces (177 mL) of methylene chloride-based stripper was used during a similar job and methylene chloride vapor concentration of 92,949 to 154,916 ppm in the bathtub and 5099 to 8499 ppm in the bathroom were estimated. It was determined that this patient was exposed to 637 to 1062 ppm of methylene chloride in the bathroom and 11,618 to 19,364 ppm of methylene chloride in the tub during 1 hour of exposure (OSHA's short-term exposure limit: 125 ppm; 8-hour permissible exposure limit: 25 ppm; NIOSH immediately dangerous to life and health level: 2300 ppm) (Centers for Disease Control and Prevention (CDC), 2012).
    e) CASE SERIES: Dichloromethane blood concentrations of 2 workers who died following inhalational exposure to paint stripping agents containing 60% to 100% of dichloromethane, were 37.8 mg/dL and 220 mg/dL, respectively (Macisaac et al, 2013).
    f) In one study, 42 bathtub stripping products from the Internet and several hardware stores contained 60% to 100% methylene chloride. OSHA has reported 13 bathtub refinisher fatalities associated with methylene chloride stripping agents in 9 states from 2000 to 2011. Blood methylene chloride concentrations of 6 patients ranged from 18 to 223 mg/L (Centers for Disease Control and Prevention (CDC), 2012).
    g) Methylene chloride concentrations in the lung tissue of two workers, who died following inhalation of paint stripping agents containing 77% and 84% methylene chloride, were 540 mg/L and 7280 mcg/mL, respectively. The methylene chloride concentration in the blood of the worker exposed to 77% methylene chloride was 140 mg/L. The methylene chloride concentrations of the blood from the left and right heart ventricles, of the other worker, were 5420 mcg/mL and 4590 mcg/mL, respectively (Fechner et al, 2001; Zarrabeitia et al, 2001).

Workplace Standards

    A) ACGIH TLV Values for CAS75-09-2 (American Conference of Governmental Industrial Hygienists, 2010):
    1) 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.
    a) Adopted Value
    1) Dichloromethane
    a) TLV:
    1) TLV-TWA: 50 ppm
    2) TLV-STEL:
    3) TLV-Ceiling:
    b) Notations and Endnotes:
    1) Carcinogenicity Category: A3
    2) Codes: BEI
    3) Definitions:
    a) 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.
    b) BEI: The BEI notation is listed when a BEI is also recommended for the substance listed. Biological monitoring should be instituted for such substances to evaluate the total exposure from all sources, including dermal, ingestion, or non-occupational.
    c) TLV Basis - Critical Effect(s): COHb-emia; CNS impair
    d) Molecular Weight: 84.93
    1) For gases and vapors, to convert the TLV from ppm to mg/m(3):
    a) [(TLV in ppm)(gram molecular weight of substance)]/24.45
    2) For gases and vapors, to convert the TLV from mg/m(3) to ppm:
    a) [(TLV in mg/m(3))(24.45)]/gram molecular weight of substance
    e) Additional information:

    B) NIOSH REL and IDLH Values for CAS75-09-2 (National Institute for Occupational Safety and Health, 2007):
    1) Listed as: Methylene chloride
    2) REL:
    a) TWA:
    b) STEL:
    c) Ceiling:
    d) Carcinogen Listing: (Ca) NIOSH considers this substance to be a potential occupational carcinogen (See Appendix A in the NIOSH Pocket Guide to Chemical Hazards).
    e) Skin Designation: Not Listed
    f) Note(s): See Appendix A
    3) IDLH:
    a) IDLH: 2300 ppm
    b) Note(s): Ca
    1) Ca: NIOSH considers this substance to be a potential occupational carcinogen (See Appendix A).

    C) Carcinogenicity Ratings for CAS75-09-2 :
    1) ACGIH (American Conference of Governmental Industrial Hygienists, 2010): A3 ; Listed as: Dichloromethane
    a) 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.
    2) EPA (U.S. Environmental Protection Agency, 2011): B2 ; Listed as: Dichloromethane
    a) B2 : Probable human carcinogen - based on sufficient evidence of carcinogenicity in animals.
    3) 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): 2A ; Listed as: Dichloromethane (methylene chloride)
    a) 2A : The agent (mixture) is probably carcinogenic to humans. The exposure circumstance entails exposures that are probably carcinogenic to humans. This category is used when there is limited evidence of carcinogenicity in humans and sufficient evidence of carcinogenicity in experimental animals. In some cases, an agent (mixture) may be classified in this category when there is inadequate evidence of carcinogenicity in humans and sufficient evidence of carcinogenicity in experimental animals and strong evidence that the carcinogenesis is mediated by a mechanism that also operates in humans. Exceptionally, an agent, mixture or exposure circumstance may be classified in this category solely on the basis of limited evidence of carcinogenicity in humans.
    4) NIOSH (National Institute for Occupational Safety and Health, 2007): Ca ; Listed as: Methylene chloride
    a) Ca : NIOSH considers this substance to be a potential occupational carcinogen (See Appendix A in the NIOSH Pocket Guide to Chemical Hazards).
    5) MAK (DFG, 2002): Category 3A ; Listed as: Dichloromethane
    a) Category 3A : Substances for which the criteria for classification in Category 4 or 5 are fulfilled but for which the database is insufficient for the establishment of a MAK value.
    6) NTP (U.S. Department of Health and Human Services, Public Health Service, National Toxicology Project ): Not Listed

    D) OSHA PEL Values for CAS75-09-2 (U.S. Occupational Safety, and Health Administration (OSHA), 2010):
    1) Listed as: Methylene chloride
    2) Table Z-1 for Methylene chloride:
    a) 8-hour TWA:
    1) ppm:
    a) Parts of vapor or gas per million parts of contaminated air by volume at 25 degrees C and 760 torr.
    2) mg/m3:
    a) Milligrams of substances per cubic meter of air. When entry is in this column only, the value is exact; when listed with a ppm entry, it is approximate.
    3) Ceiling Value:
    4) Skin Designation: No
    5) Notation(s): Not Listed
    3) Table Z-2 for Methylene Chloride: See section 1919.1052:
    a) 8-hour TWA:
    b) Acceptable Ceiling Concentration:
    c) Acceptable Maximum Peak above the Ceiling Concentration for an 8-hour Shift:
    1) Concentration:
    2) Maximum Duration:
    d) Notation(s): Not Listed

Toxicity Information

    7.7.1) TOXICITY VALUES
    A) References: Hayes, 1991 HSDB, 2002 Lewis, 2000 OHM/TADS, 2002 RTECS, 2002
    1) LD50- (INHALATION)MOUSE:
    a) 16,000 ppm for 7H plus 1H observation (HSDB, 2002)
    2) LD50- (INTRAPERITONEAL)MOUSE:
    a) 437 mg/kg
    3) LD50- (ORAL)MOUSE:
    a) 873 mg/kg
    4) LD50- (SUBCUTANEOUS)MOUSE:
    a) 6460 mg/kg
    5) LD50- (INTRAPERITONEAL)RAT:
    a) 916 mg/kg
    b) 2000 ppm (OHM/TADS, 2002)
    6) LD50- (ORAL)RAT:
    a) 1600 mg/kg -- ataxia
    b) 14D old, 2385 mg/kg (Hayes, 1991)
    c) young adult, 2120 mg/kg (Hayes, 1991)
    d) older adult, 3047 mg/kg (Hayes, 1991)
    e) 1600 mg/kg (HSDB, 2002)
    f) 3000 mg/kg (HSDB, 2002)
    7) TCLo- (INHALATION)HUMAN:
    a) 500 ppm for 1Y - intermittent -- altered sleep time; somnolence; change in heart rate
    b) 500 ppm for 8H -- behaviorial changes
    8) TCLo- (INHALATION)MOUSE:
    a) 2000 ppm for 5H/2Y - continuous -- carcinogenic; tumors
    b) Female, 1250 ppm for 7H at 6-15D of pregnancy -- musculoskeletal system abnormalities
    c) 150 ppm for 24H/30D - continuous -- changes in liver, spleen weight; biochemical changes
    d) 300 ppm for 24H/90D - continuous -- liver and spleen weight changes; biochemical changes
    e) 13,000 ppm for 6H/19D - intermittent -- death
    f) 5000 ppm for 24H/7D - continuous -- liver weight changes; weight loss or decreased weight gain
    9) TCLo- (INHALATION)RAT:
    a) Female, 4500 ppm for 24H at 1-17D of pregnancy -- behavioral effects on newborn
    b) 3500 ppm for 6H/2Y - intermittent -- carcinogenic; tumors
    c) 500 ppm for 6H/2Y (Lewis, 2000)
    d) 1000 ppm for 2H/3W - intermittent -- behavioral, liver, and blood changes
    e) 5000 ppm for 24H/14W - continuous -- liver changes; chages in tubules and bladder weight
    f) 8400 ppm for 6H/13W - intermittent -- changes in liver wright; death
    g) 500 ppm for 6H/2W - intermittent -- kidney, ureter and bladder changes; blood and biochemical changes
    h) 3700 ppm for 5H/4W - intermittent -- biochemical changes; lung, thorax, or respiration changes
    i) 1000 ppm for 6H/3D - intermittent -- brain and coverings changes; biochemical effects

Toxicologic Mechanism

    A) Methylene chloride is an anesthetic that causes CNS depression at high concentrations (Lewis, 1998).
    B) METABOLITE -
    1) The compound is converted in part to carbon monoxide, and carboxyhemoglobin is increased in the blood of exposed individuals (Baselt, 1997).
    a) Concentrations of carboxyhemoglobin rose from 4.5 to 9 percent after 8 hours of exposure in a methylene chloride atmosphere of 180 to 200 ppm (Ratney et al, 1974).
    2) The conversion of methylene chloride to carbon monoxide and formation of carboxyhemoglobin may continue for several hours after exposure has ended(Rioux & Myers, 1989; Mahmud & Kales, 1999).
    3) Methylene chloride demonstrates a linear dose-response relationship between duration and intensity of exposure. A constant methylene chloride air concentration of 180 ppm increases carboxyhemoglobin at 0.5 percent per hour (Mahmud & Kales, 1999).
    4) Shusterman et al (1990) noted carboxyhemoglobin saturations between 10 and 11 percent after a 6.5- to 7.5-hour exposure to methylene chloride at 350 ppm.
    C) COMBUSTION PRODUCTS - When heated to decomposition, methylene chloride releases hydrogen chloride as well as small amounts of phosgene and chlorine (Lewis, 1996; Gerritsen & Buschmann, 1960; Little, 1955; Noweir et al, 1972).

Physical Characteristics

    A) Methylene chloride is a colorless, volatile (but not flammable in air) liquid with a sweet, penetrating, ether-like or chloroform-like odor (ACGIH, 1991; Lewis, 2000) AAR, 1998).

Ph

    A) Not Applicable

Molecular Weight

    A) 84.93

Other

    A) ODOR THRESHOLD
    1) The threshold ranges from 25 to 150 ppm; 100 ppm is not easily detectable by most people, and above 300 ppm most people detect the odor. This means that odor is a poor indicator of possibly dangerous air concentrations of methylene chloride (the TLV is 50 ppm) (ACGIH, 1991; Sittig, 1991).
    2) 160-620 ppm; 540-2160 mg/m(3) (in air) (ATSDR, 1993)
    3) 9.1 ppm (in water) (ATSDR, 1993)
    4) 205-307 ppm (CHRIS , 2002; HSDB , 2002)
    5) 25-50 ppm (OHM/TADS , 2002)
    6) 214 ppm (recognition in air) (HSDB , 2002)
    7) low = 540 mg/m(3); high = 2,160 mg/m(3) (HSDB , 2002)
    8) 743 mg/m(3) (IPCS, 1996)
    9) 700-1060 mg/m(3) (IPCS, 1996)
    10) 880 mg/m(3) (IPCS, 1996)
    11) 540-2160 mg/m(3) (IPCS, 1996)
    12) At concentrations above 300 ppm, methylene chloride has a "not unpleasant odor". At concentrations above 1000 ppm, the odor becomes unpleasant, and is strong and intensely irritating at 2300 ppm (Bingham et al, 2001).

General Bibliography

    1) 40 CFR 372.28: Environmental Protection Agency - Toxic Chemical Release Reporting, Community Right-To-Know, Lower thresholds for chemicals of special concern. National Archives and Records Administration (NARA) and the Government Printing Office (GPO). Washington, DC. Final rules current as of Apr 3, 2006.
    2) 40 CFR 372.65: Environmental Protection Agency - Toxic Chemical Release Reporting, Community Right-To-Know, Chemicals and Chemical Categories to which this part applies. National Archives and Records Association (NARA) and the Government Printing Office (GPO), Washington, DC. Final rules current as of Apr 3, 2006.
    3) 49 CFR 172.101 - App. B: Department of Transportation - Table of Hazardous Materials, Appendix B: List of Marine Pollutants. National Archives and Records Administration (NARA) and the Government Printing Office (GPO), Washington, DC. Final rules current as of Aug 29, 2005.
    4) 49 CFR 172.101: Department of Transportation - Table of Hazardous Materials. National Archives and Records Administration (NARA) and the Government Printing Office (GPO), Washington, DC. Final rules current as of Aug 11, 2005.
    5) 62 FR 58840: Notice of the National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances - Proposed AEGL Values, Environmental Protection Agency, NAC/AEGL Committee. National Archives and Records Administration (NARA) and the Government Publishing Office (GPO), Washington, DC, 1997.
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