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OCCUPATIONAL SAFETY AND HEALTH GUIDELINE FOR ETHYL CHLORIDE
Disclaimer: These guidelines were developed under contract using generally accepted secondary sources. The protocol used by the contractor for surveying these data sources was developed by the National Institute for Occupational Safety and Health (NIOSH), the Occupational Safety and Health Administration (OSHA), and the Department of Energy (DOE). The information contained in these guidelines is intended for reference purposes only. None of the agencies have conducted a comprehensive check of the information and data contained in these sources. It provides a summary of information about chemicals that workers may be exposed to in their workplaces. The secondary sources used for supplements 111 and 1V were published before 1992 and 1993, respectively, and for the remainder of the guidelines the secondary sources used were published before September 1996. This information may be superseded by new developments in the field of industrial hygiene. Therefore readers are advised to determine whether new information is available.

INTRODUCTION

This guideline summarizes pertinent information about ethyl chloride for workers and employers as well as for physicians, industrial hygienists, and other occupational safety and health professionals who may need such information to conduct effective occupational safety and health programs. Recommendations may be superseded by new developments in these fields; readers are therefore advised to regard these recommendations as general guidelines and to determine whether new information is available.

SUBSTANCE IDENTIFICATION

* Formula
C(2)H(5)Cl
* Structure
(For Structure, see paper copy)
* Synonyms
Chloroethane, monochloroethane, hydrochloric ether, muriatic ether, chlorethyl, chloryl anesthetic
* Identifiers
  1. CAS No.: 75-00-3
  2. RTECS No.: KH7525000
  3. DOT UN: 1037 27
  4. DOT label: Flammable gas
* Appearance and odor
Ethyl chloride is a gas at room temperature and a volatile liquid when compressed, or at lower temperatures. It has a pungent, ether-like odor. The air odor threshold concentration for ethyl chloride has been reported as 4.2 parts per million (ppm) parts of air.
CHEMICAL AND PHYSICAL PROPERTIES

* Physical data
  1. Molecular weight: 64.52
  2. Boiling point (at 760 mm Hg): 12.3 degrees C (54.14 degrees F)
  3. Specific gravity: 0.92 at 0 degrees C (32 degrees F)
  4. Vapor density: 2.22
  5. Melting point: -138.7 degrees C (-217.66 degrees F)
  6. Vapor pressure at 20 degrees C (68 degrees F): 1064 mm Hg
  7. Solubility: Slightly soluble in water; miscible with most organic solvents.
  8. Evaporation rate (butyl acetate = 1): Greater than 1.0
* Reactivity
  1. Conditions contributing to instability: Heat, sparks, or open flames.
  2. Incompatibilities: Contact between ethyl chloride and chemically active metals such as sodium, potassium, calcium, powdered aluminum, zinc, and magnesium may cause fires and explosions. Ethyl chloride reacts vigorously with oxidizing materials. Contact with water, steam, or alkalis may produce toxic and corrosive fumes.
Hazardous decomposition products: Toxic gases and vapors (such as hydrogen chloride, phosgene, and carbon monoxide) may be released in a fire involving ethyl chloride.
Special precautions: None reported.
* Flammability
The National Fire Protection Association has assigned a flammability rating of 4 (extreme fire hazard) to ethyl chloride.
  1. Flash point: -43 degrees C (-45.4 degrees F) (open cup)
  2. Autoignition temperature: 519 degrees C (966 degrees F)
  3. Flammable limits in air (percent by volume): Lower, 3.8; upper, 15.4
  4. Extinguishant: Dry chemical, carbon dioxide, water spray, or standard foam for small fires. Use water spray, fog, or standard foam for large fires. Do not use a stream of water because it will scatter and spread the fire; however, water spray may be used to cool cylinders or containers.
Fires involving ethyl chloride should be fought upwind from the maximum distance possible. Keep unnecessary people away; isolate the hazard area and deny entry. Isolate the area for 1/2 mile in all directions if a tank, rail car, or tank truck is involved in the fire. For a massive fire in a cargo area, use unmanned hose holders or monitor nozzles; if this is impossible, withdraw from the area and let the fire burn. Emergency personnel should stay out of low areas and ventilate closed spaces before entering. Vapors may travel to a source of ignition and flash back. Vapors are an explosion and poison hazard indoors, outdoors, or in sewers. Containers of ethyl chloride may explode in the heat of the fire and should be moved from the fire area if it is possible to do so safely. If this is not possible, cool fire exposed containers from the sides with water until well after the fire is out. Do not get water inside the containers. Stay away from the ends of containers. Personnel should withdraw immediately if a rising sound from a venting safety device is heard or if there is discoloration of a container due to fire. Firefighters should wear a full set of protective clothing and self-contained breathing apparatus when fighting fires involving ethyl chloride.
EXPOSURE LIMITS

* OSHA PEL
The current Occupational Safety and Health Administration (OSHA) permissible exposure limit (PEL) for ethyl chloride is 1000 ppm (2600 milligrams per cubic meter (mg/m(3))) as an 8-hour time-weighted average (TWA) concentration [29 CFR 1910.1000, Table Z-1].
* NIOSH REL
The National Institute for Occupational Safety and Health (NIOSH) has not established a concentration for the recommended exposure limit (REL) for ethyl chloride, but lists the REL as "handle with caution in the workplace" [NIOSH 1992].
* ACGIH TLV
The American Conference of Governmental Industrial Hygienists (ACGIH) has assigned ethyl chloride a threshold limit value (TLV) of 100 ppm (2640 mg/m(3)) as a TWA for a normal 8-hour workday and a 40-hour workweek [ACGIH 1994, p. 21].
* Rationale for Limits
The NIOSH REL is based on the risk of cancer, cancer effects, possible liver and kidney effects [NIOSH 1992].
The ACGIH limit is based on the risk of narcosis [ACGIH 1991, p. 595].

HEALTH HAZARD INFORMATION

* Routes of Exposure
Exposure to ethyl chloride can occur through inhalation, ingestion, and skin contact [Sittig 1991, p. 749].
* Summary of toxicology
  1. Effects on Animals: Ethyl chloride produces narcosis and pathological alterations in the liver, kidneys, lungs, and heart of exposed animals. The lowest lethal concentration for rats is 160 gm/m(3) for a 2-hour exposure and 4,500 ppm for a 45-minute exposure in guinea pigs [NIOSH 1991]. Exposure to 23 or 24 percent ethyl chloride in air caused guinea pigs to lose consciousness in 5 to 10 minutes; some of the animals died from this exposure. At 9,000 ppm ethyl chloride, all guinea pigs survived, but histopathological changes were noted in the liver, kidneys, and lungs. In guinea pigs exposed to 40,000 ppm ethyl chloride, incoordination was seen after 3 minutes and eye irritation and inability to stand were noted within 40 minutes. However, all animals survived 4.5 hours of exposure at this level, although some died within 9 hours. Pathological changes in the liver, lungs, and kidneys were observed [ACGIH 1991]. Rats subjected to a 2-hour anesthesia with ethyl chloride experienced a complete disappearance of glycogen in the liver, a decrease in acid phosphatase levels, and increases in alkaline phosphates and succinic dehydrogenase levels [ACGIH 1991]. Liquid ethyl chloride sprayed into the eyes of rabbits damaged the cornea [Grant 1986].
  2. Effects on Humans: Ethyl chloride is a mild irritant of the eyes, mucous membranes, and respiratory tract and is also a narcotic. It is absorbed through the mucous membranes and quickly eliminated through the lungs [Parmeggiani 1983]. The inhalation of a 0.1 percent concentration of ethyl chloride does not produce narcosis in humans [Parmeggiani 1983]. Intoxication began at 1.3 percent and increased at increasing dosages. At a dose of 3.36 percent, noisy talkativeness and incoordination was followed by cyanosis, nausea, and vomiting during recovery. Memory loss was induced at 1.9% and increased at increasing dosages [ACGIH 1991]. In another study, inhalation of 40,000 ppm by human subjects produced dizziness, eye irritation and stomach cramp, whereas inhalation of 25,000 ppm caused incoordination [Hathaway et al. 1991]. During an allergy testing procedure, two individuals developed acute allergic eczematous dermatitis after ethyl chloride [Clayton and Clayton 1982]. Liquefied ethyl chloride spilled on the skin or eye may cause frostbite [Parmeggiani 1983].
* Signs and symptoms of exposure
  1. Acute exposure: Acute overexposures to ethyl chloride may result in subjective feeling of intoxication, headache, loss of coordination, salivation, analgesia, stomach cramps, depression of respiration, and stupor [Sittig 1991; Genium 1993]. Liquid ethyl chloride spilled on the skin or into the eye may cause frostbite with whitening of the tissue and numbness, followed by pain, redness, and blistering.
  2. Chronic exposure: Chronic exposure to ethyl chloride may result in allergic eczematous dermatitis [Clayton and Clayton 1982].
EMERGENCY MEDICAL PROCEDURES

* Emergency medical procedures: [NIOSH to supply]
  1. Rescue: Remove an incapacitated worker from further exposure and implement appropriate emergency procedures (e.g., those listed on the Material Safety Data Sheet required by OSHA's Hazard Communication Standard [29 CFR 1910.1200]). All workers should be familiar with emergency procedures, the location and proper use of emergency equipment, and methods of protecting themselves during rescue operations.
EXPOSURE SOURCES AND CONTROL METHODS

The following operations may involve ethyl chloride and lead to worker exposures to this substance:

* The manufacture and transportation of ethyl chloride
* Use as a local anesthetic and formerly as a general anesthetic; used as a refrigerant; used as a solvent for fats, oils, waxes, phosphorus, sulfur, acetylene, and many resins
* Use in organic synthesis of perchloroethane, ester, Grignard reagents, tetraethyl lead, dyes, drugs, perfumes, and ethyl cellulose
* Use as a propellant in aerosols
* Use as an insecticide
Methods that are effective in controlling worker exposures to ethyl chloride, depending on the feasibility of implementation, are as follows:
* Process enclosure
* Local exhaust ventilation
* General dilution ventilation
* Personal protective equipment

Workers responding to a release or potential release of a hazardous substance must be protected as required by paragraph (q) of OSHA's Hazardous Waste Operations and Emergency Response Standard [29 CFR 1910.120].

Good sources of information about control methods are as follows:
  1. ACGIH [1992]. Industrial ventilation--a manual of recommended practice. 21st ed. Cincinnati, OH: American Conference of Governmental Industrial Hygienists.
  2. Burton DJ [1986]. Industrial ventilation--a self study companion. Cincinnati, OH: American Conference of Governmental Industrial Hygienists.
  3. Alden JL, Kane JM [1982]. Design of industrial ventilation systems. New York, NY: Industrial Press, Inc.
  4. Wadden RA, Scheff PA [1987]. Engineering design for control of workplace hazards. New York, NY: McGraw-Hill.
  5. Plog BA [1988]. Fundamentals of industrial hygiene. Chicago, IL: National Safety Council.
MEDICAL SURVEILLANCE

OSHA is currently developing requirements for medical surveillance. When these requirements are promulgated, readers should refer to them for additional information and to determine whether employers whose employees are exposed to ethyl chloride are required to implement medical surveillance procedures.

* Medical Screening
Workers who may be exposed to chemical hazards should be monitored in a systematic program of medical surveillance that is intended to prevent occupational injury and disease. The program should include education of employers and workers about work-related hazards, early detection of adverse health effects, and referral of workers for diagnosis and treatment. The occurrence of disease or other work-related adverse health effects should prompt immediate evaluation of primary preventive measures (e.g., industrial hygiene monitoring, engineering controls, and personal protective equipment). A medical surveillance program is intended to supplement, not replace, such measures. To detect and control work-related health effects, medical evaluations should be performed (1) before job placement, (2) periodically during the term of employment, and (3) at the time of job transfer or termination.
* Preplacement medical evaluation
Before a worker is placed in a job with a potential for exposure to ethyl chloride, a licensed health care professional should evaluate and document the worker's baseline health status with thorough medical, environmental, and occupational histories, a physical examination, and physiologic and laboratory tests appropriate for the anticipated occupational risks. These should concentrate on the function and integrity of the liver, kidneys, respiratory system, and cardiovascular system. Medical surveillance for respiratory disease should be conducted using the principles and methods recommended by the American Thoracic Society.
A preplacement medical evaluation is recommended to assess medical conditions that may be aggravated or may result in increased risk when a worker is exposed to ethyl chloride at or below the prescribed exposure limit. The health care professional should consider the probable frequency, intensity, and duration of exposure as well as the nature and degree of any applicable medical condition. Such conditions (which should not be regarded as absolute contraindications to job placement) include a history and other findings consistent with diseases of the liver, kidneys, respiratory system, and cardiovascular system.
* Periodic medical evaluations
Occupational health interviews and physical examinations should be performed at regular intervals during the employment period, as mandated by any applicable Federal, State, or local standard. Where no standard exists and the hazard is minimal, evaluations should be conducted every 3 to 5 years or as frequently as recommended by an experienced occupational health physician. Additional examinations may be necessary if a worker develops symptoms attributable to ethyl chloride exposure. The interviews, examinations, and medical screening tests should focus on identifying the adverse effects of ethyl chloride on the liver, kidneys, respiratory system, and cardiovascular system. Current health status should be compared with the baseline health status of the individual worker or with expected values for a suitable reference population.
* Termination medical evaluations
The medical, environmental, and occupational history interviews, the physical examination, and selected physiologic or laboratory tests that were conducted at the time of placement should be repeated at the time of job transfer or termination to determine the worker's medical status at the end of his or her employment. Any changes in the worker's health status should be compared with those expected for a suitable reference population. Because occupational exposure to ethyl chloride may cause diseases with prolonged latent periods, the need for medical surveillance may extend well beyond the termination of employment.
* Biological monitoring
Biological monitoring involves sampling and analyzing body tissues or fluids to provide an index of exposure to a toxic substance or metabolite. No biological monitoring test acceptable for routine use has yet been developed for ethyl chloride.
WORKPLACE MONITORING AND MEASUREMENT

Determination of a worker's exposure to airborne ethyl chloride is made using charcoal tubes in series (front tube 400 mg section, back tube 200 mg section, both 20/40 mesh). Samples are collected at a maximum flow rate of 0.05 liter/minute until a maximum collection volume of 3 liters is reached. The sample is then treated with carbon disulfide. Analysis is conducted by gas chromatography using a flame ionization detector (GC/FID). This method is fully validated and is described in the OSHA Computerized Information System [OSHA 1994] and in NIOSH Method No. 2519 [NIOSH 1994].

PERSONAL HYGIENE PROCEDURES

If ethyl chloride contacts the skin, workers should flush the affected areas immediately with plenty of water, followed by washing with soap and water.

Clothing contaminated with ethyl chloride should be removed immediately, and provisions should be made for the safe removal of the chemical from the clothing. Persons laundering the clothes should be informed of the hazardous properties of ethyl chloride, particularly its potential for causing systemic toxicity.

A worker who handles ethyl chloride should thoroughly wash hands, forearms, and face with soap and water before eating, using tobacco products, using toilet facilities, applying cosmetics, or taking medication.

Workers should not eat, drink, use tobacco products, apply cosmetics, or take medication in areas where ethyl chloride or a solution containing ethyl chloride is handled, processed, or stored.

STORAGE

Ethyl chloride should be stored in a cool, dry, well-ventilated area in tightly sealed containers that are labeled in accordance with OSHA's Hazard Communication Standard [29 CFR 1910.1200]. Containers of ethyl chloride should be protected from physical damage and water or steam, and should be stored separately from chemically active metals such as sodium, potassium, calcium, powdered aluminum, zinc, and magnesium, oxidizing materials, or alkalis.

SPILLS AND LEAKS

In the event of a spill or leak involving ethyl chloride, persons not wearing protective equipment and clothing should be restricted from contaminated areas until cleanup has been completed. The following steps should be undertaken following a spill or leak:
  1. Notify safety personnel.
  2. Remove all sources of heat and ignition.
  3. Ventilate potentially explosive atmospheres.
  4. Do not touch the spilled material; stop the leak if it is possible to do so without risk.
  5. Use non-sparking tools.
  6. Water spray may be used to reduce vapors, but the spray may not prevent ignition in closed spaces.
  7. For small liquid spills, take up with sand or other noncombustible absorbent material and place into closed containers for later disposal.
  8. For large liquid spills, build dikes far ahead of the spill to contain the ethyl chloride for later reclamation or disposal.
  9. Prevent flushing ethyl chloride to sewers, drains, and waterways.
SPECIAL REQUIREMENTS

U.S. Environmental Protection Agency (EPA) requirements for emergency planning, reportable quantities of hazardous releases, community right-to-know, and hazardous waste management may change over time. Users are therefore advised to determine periodically whether new information is available.

* Emergency planning requirements
Ethyl chloride is not subject to EPA emergency planning requirements under the Superfund Amendments and Reauthorization Act (SARA) (Title III) in 42 USC 11022.
* Reportable quantity requirements for hazardous releases
A hazardous substance release is defined by EPA as any spilling, leaking, pumping, pouring, emitting, emptying, discharging, injecting, escaping, leaching, dumping, or disposing into the environment (including the abandonment or discarding of contaminated containers) of hazardous substances. In the event of a release that is above the reportable quantity for that chemical, employers are required to notify the proper Federal, State, and local authorities [40 CFR 355.40].
The reportable quantity of ethyl chloride is 100 pounds. If an amount equal to or greater than this quantity is released within a 24-hour period in a manner that will expose persons outside the facility, employers are required to do the following: - Notify the National Response Center immediately at (800) 424-8802 or at (202) 426-2675 in Washington, D.C. [40 CFR 302.6].
* Community right-to-know requirements
Employers who own or operate facilities in SIC codes 20 to 39 that employ 10 or more workers and that manufacture 25,000 pounds or more of ethyl chloride per calendar year or otherwise use 10,000 pounds or more of ethyl chloride per calendar year are required by EPA [40 CFR Part 372.30] to submit a Toxic Chemical Release Inventory form (Form R) to EPA reporting the amount of ethyl chloride emitted or released from their facility annually.
* Hazardous waste management requirements
EPA considers a waste to be hazardous if it exhibits any of the following characteristics: ignitability, corrosivity, reactivity, or toxicity as defined in 40 CFR 261.21-261.24. Under the Resource Conservation and Recovery Act (RCRA) [40 USC 6901 et seq.], EPA has specifically listed many chemical wastes as hazardous. Although ethyl chloride is not specifically listed as a hazardous waste under RCRA, EPA requires employers to treat waste as hazardous if it exhibits any of the characteristics discussed above.
Providing detailed information about the removal and disposal of specific chemicals is beyond the scope of this guideline. The U.S. Department of Transportation, EPA, and State and local regulations should be followed to ensure that removal, transport, and disposal of this substance are conducted in accordance with existing regulations. To be certain that chemical waste disposal meets EPA regulatory requirements, employers should address any questions to the RCRA hotline at (703) 412-9810 (in the Washington, D.C. area) or toll-free at (800) 424-9346 (outside Washington, D.C.). In addition, relevant State and local authorities should be contacted for information on any requirements they may have for the waste removal and disposal of this substance.
RESPIRATORY PROTECTION

* Conditions for respirator use
Good industrial hygiene practice requires that engineering controls be used where feasible to reduce workplace concentrations of hazardous materials to the prescribed exposure limit. However, some situations may require the use of respirators to control exposure. Respirators must be worn if the ambient concentration of ethyl chloride exceeds prescribed exposure limits. Respirators may be used (1) before engineering controls have been installed, (2) during work operations such as maintenance or repair activities that involve unknown exposures, (3) during operations that require entry into tanks or closed vessels, and (4) during emergencies. Workers should only use respirators that have been approved by NIOSH and the Mine Safety and Health Administration (MSHA).
* Respiratory protection program
Employers should institute a complete respiratory protection program that, at a minimum, complies with the requirements of OSHA's Respiratory Protection Standard [29 CFR 1910.134]. Such a program must include respirator selection, an evaluation of the worker's ability to perform the work while wearing a respirator, the regular training of personnel, respirator fit testing, periodic workplace monitoring, and regular respirator maintenance, inspection, and cleaning. The implementation of an adequate respiratory protection program (including selection of the correct respirator) requires that a knowledgeable person be in charge of the program and that the program be evaluated regularly. For additional information on the selection and use of respirators and on the medical screening of respirator users, consult the latest edition of the NIOSH Respirator Decision Logic [NIOSH 1987b] and the NIOSH Guide to Industrial Respiratory Protection [NIOSH 1987a].
PERSONAL PROTECTIVE EQUIPMENT

Workers should use appropriate personal protective clothing and equipment that must be carefully selected, used, and maintained to be effective in preventing skin contact with ethyl chloride. The selection of the appropriate personal protective equipment (PPE) (e.g., gloves, sleeves, encapsulating suits) should be based on the extent of the worker's potential exposure to ethyl chloride. There are no published reports on the resistance of various materials to permeation by ethyl chloride.
To evaluate the use of PPE materials with ethyl chloride, users should consult the best available performance data and manufacturers' recommendations. Significant differences have been demonstrated in the chemical resistance of generically similar PPE materials (e.g., butyl) produced by different manufacturers. In addition, the chemical resistance of a mixture may be significantly different from that of any of its neat components.

Any chemical-resistant clothing that is used should be periodically evaluated to determine its effectiveness in preventing dermal contact. Safety showers and eye wash stations should be located close to operations that involve ethyl chloride.
Splash-proof chemical safety goggles or face shields (20 to 30 cm long, minimum) should be worn during any operation in which a solvent, caustic, or other toxic substance may be splashed into the eyes.

In addition to the possible need for wearing protective outer apparel (e.g., aprons, encapsulating suits), workers should wear work uniforms, coveralls, or similar full-body coverings that are laundered each day. Employers should provide lockers or other closed areas to store work and street clothing separately. Employers should collect work clothing at the end of each work shift and provide for its laundering. Laundry personnel should be informed about the potential hazards of handling contaminated clothing and instructed about measures to minimize their health risk.

Protective clothing should be kept free of oil and grease and should be inspected and maintained regularly to preserve its effectiveness.

Protective clothing may interfere with the body's heat dissipation, especially during hot weather or during work in hot or poorly ventilated work environments.

REFERENCES

ACGIH [1991]. Documentation of the threshold limit values and biological exposure indices. 6th ed. Cincinnati, OH: American Conference of Governmental Industrial Hygienists.

ACGIH [1994]. 1994-1995 Threshold limit values for chemical substances and physical agents and biological exposure indices. Cincinnati, OH: American Conference of Governmental Industrial Hygienists.

Amoore JE, Hautala E [1983]. Odor as an aid to chemical safety: odor thresholds compared with threshold limit values and volatilities for 214 industrial chemicals in air and water dilution. J of App Tox 3(6):272-290.

ATS [1987]. Standardization of spirometry -- 1987 update. American Thoracic Society. Am Rev Respir Dis 136:1285-1296.

CFR. Code of Federal regulations. Washington, DC: U.S. Government Printing Office, Office of the Federal Register.

Clayton G, Clayton F [1981-1982]. Patty's industrial hygiene and toxicology. 3rd rev. ed. New York, NY: John Wiley & Sons.

DOT [1993]. 1993 Emergency response guidebook, guide 27. Washington, DC: U.S. Department of Transportation, Office of Hazardous Materials Transportation, Research and Special Programs Administration.

Genium [1993]. Material safety data sheet No. 538. Schenectady, NY: Genium Publishing Corporation.

Grant WM [1986]. Toxicology of the eye. 3rd ed. Springfield, IL: Charles C Thomas.

Hathaway GJ, Proctor NH, Hughes JP, and Fischman ML [1991]. Proctor and Hughes' chemical hazards of the workplace. 3rd ed. New York, NY: Van Nostrand Reinhold.

Lewis RJ, ed. [1993]. Lewis condensed chemical dictionary. 12th ed. New York, NY: Van Nostrand Reinhold Company.

Mickelsen RL, Hall RC [1987]. A breakthrough time comparison of nitrile and neoprene glove materials produced by different glove manufacturers. Am Ind Hyg Assoc J 48(11): 941-947.

Mickelsen RL, Hall RC, Chern RT, Myers JR [1991]. Evaluation of a simple weight-loss method for determining the permeation of organic liquids through rubber films. Am Ind Hyg Assoc J 52(10): 445-447.

NFPA [1986]. Fire protection guide on hazardous materials. 9th ed. Quincy, MA: National Fire Protection Association.

NIOSH [1987a]. NIOSH guide to industrial respiratory protection. Cincinnati, OH: U.S. Department of Health and Human Services, Public Health Service, Centers for Disease Control, National Institute for Occupational Safety and Health, DHHS (NIOSH) Publication No. 87-116.
 
NIOSH [1987b]. NIOSH respirator decision logic. Cincinnati, OH: U.S. Department of Health and Human Services, Public Health Service, Centers for Disease Control, National Institute for Occupational Safety and Health, DHHS (NIOSH) Publication No. 87-108.

NIOSH [1991]. Registry of toxic effects of chemical substances: Ethyl Chloride. Cincinnati, OH: U.S. Department of Health and Human Services, Public Health Service, Centers for Disease Control, National Institute for Occupational Safety and Health, Division of Standards Development and Technology Transfer, Technical Information Branch.

NIOSH [1992]. Recommendations for occupational safety and health: Compendium of policy documents and statements. Cincinnati, OH: U.S. Department of Health and Human Services, Public Health Service, Centers for Disease Control, National Institute for Occupational Safety and Health, DHHS (NIOSH) Publication No. 92-100.

NIOSH [1994]. NIOSH manual of analytical methods. 4th ed. Cincinnati, OH: U.S. Department of Health and Human Services, Public Health Service, Centers for Disease Control, National Institute for Occupational Safety and Health, DHHS (NIOSH) Publication No. 94-113.

NJDH [1985]. Hazardous substance fact sheet: Ethyl Chloride. Trenton, NJ: New Jersey Department of Health.

NLM [1992]. Hazardous substances data bank: Ethyl Chloride. Bethesda, MD: National Library of Medicine.

OSHA [1994]. Computerized information system. Washington, DC: U.S. Department of Labor, Occupational Safety and Health Administration.

Parmeggiani L [1983]. Encyclopedia of occupational health and safety. 3rd rev. ed. Geneva, Switzerland: International Labour Organisation.

Patnaik P [1992]. A comprehensive guide to the hazardous properties of chemical substances. New York, NY: Van Nostrand Reinhold.

Sittig M [1991]. Handbook of toxic and hazardous chemicals. 3rd ed. Park Ridge, NJ: Noyes Publications.

USC. United States code. Washington, DC: U.S. Government Printing Office.

Windholz M, ed. [1983]. Windholz Index 10th ed. Rahway, NJ: Windholz & Company.
 
 
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