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 This information may be superseded by new developments in the field of industrial hygiene.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.

OCCUPATIONAL SAFETY AND HEALTH GUIDELINE FOR 1,2-DICHLOROETHYLENE

INTRODUCTION

This guideline summarizes pertinent information about 1,2-dichloroethylene 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 Recommendations may be superseded by new developments in these fields; readers are therefore advised to regard these recommendations as general guidelines and to determine whether new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(2)Cl(2)

* Structure

(For Structure, see paper copy)

* Synonyms

Acetylene dichloride; dioform; 1,2-dichloroethylene;

sym-dichloroethylene; 1,2-dichloroethene; 1,2-dichloroethene;

1,2-DCE

* Identifiers

1. CAS No.: 540-59-0 (sym); 156-59-2 (cis); 156-60-5 (trans)

2. RTECS No.: KV9360000 (sym); KV9420000 (cis); KV9400000 (trans)

3. DOT UN: 1150 29

4. DOT label: Flammable liquid

* Appearance and odor

1,2-Dichloroethylene is a colorless, volatile liquid with an ether-like, slightly acrid odor. The commercial product is available as either the cis- or trans-isomer or a mixture of the two isomers. The trans isomer has an odor threshold concentration of 17 parts per million (ppm) parts of air.

CHEMICAL AND PHYSICAL PROPERTIES

* Physical data

1. Molecular weight: 96.95

2. Boiling point (at 760 mm Hg): 60.3 degrees C (140.54 degrees F) (cis); 47.5 degrees C (117.5) (trans)

3. Specific gravity (water = 1): 1.28 (cis); 1.26 (trans)

4. Vapor density: 3.34

5. Melting point: -50 degrees C (-58 degrees F) (trans); -80.5 degrees C (-112.9 degrees F) (cis)

6. Vapor pressure: Data not available.

7. Solubility: Insoluble in water; soluble in alcohol, ether, acetone, benzene, and chloroform.

8. Evaporation rate: Data not available.

* Reactivity

1. Conditions contributing to instability: Heat, flame, or other ignition sources; light, air, or moisture will gradually decompose 1,2-dichloroethylene. The commercial product usually contains an inhibitor to prevent polymerization.

2. Incompatibilities: Contact between 1,2-dichloroethylene and strong oxidizers, strong alkalies, potassium hydroxide, or copper may cause violent reactions.

3. Hazardous decomposition products: Toxic gases such as hydrogen chloride may be released in a fire involving 1,2-dichloroethylene.

4. Special precautions: Use only non-sparking tools during the transfer or handling of 1,2-dichloroethylene.

* Flammability

The National Fire Protection Association has assigned a flammability rating of 3 (serious fire hazard) to 1,2-dichloroethylene.

1. Flash point: 2 to 3.9 degrees C (36 to 39 degrees F) (closed cup).

2. Autoignition temperature: 460 degrees C (860 degrees F).

3. Flammable limits in air (percent by volume): Lower, 5.6; upper, 12.8.

4. Extinguishant: For small fires use dry chemical, carbon dioxide, water spray, or standard foam. Use water spray, fog, or standard foam to fight large fires involving 1,2-dichloroethylene.

Fires involving 1,2-dichloroethylene 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. 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 1,2-dichloroethylene 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 1,2-dichloroethylene.

EXPOSURE LIMITS

* OSHA PEL

The current Occupational Safety and Health Administration (OSHA) permissible exposure limit (PEL) for 1,2-dichloroethylene is 200 ppm (790 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 established a recommended exposure limit (REL) for 1,2-dichloroethylene of 200 ppm (790 mg/m(3)) as a TWA for up to a 10-hour workday and a 40-hour workweek [NIOSH 1992].

* ACGIH TLV

The American Conference of Governmental Industrial Hygienists (ACGIH) has assigned 1,2-dichloroethylene a threshold limit value (TLV) of 200 ppm (793 mg/m(3)) as a TWA for a normal 8-hour workday and a 40-hour workweek [ACGIH 1994, p. 18].

* Rationale for Limits

The NIOSH limit is based on the risk of narcotic effects and mucous membrane irritation [NIOSH 1992].

The ACGIH limit is based on the no-effect level of 1,000 ppm in animals [ACGIH 1991, p. 430].

HEALTH HAZARD INFORMATION

* Routes of Exposure

Exposure to 1,2-dichloroethylene can occur through inhalation, ingestion, and eye or skin contact [Sittig 1991].

* Summary of toxicology

1. Effects on Animals: 1,2-Dichloroethylene vapor is a central nervous system depressant and a mild irritant of the mucous membranes [ACGIH 1991; Hathaway et al. 1991]. The acute oral LD(50) for a 60:40 cis-trans mixture in rats is reported as greater than 2,000 mg/kg [Clayton and Clayton 1982]. Inhalation exposure to 16,000 ppm for 4 hours was lethal to rats, but 8-minute exposures to the same concentration produced anesthesia [Clayton and Clayton 1982]. Chronic exposure studies have shown that repeated inhalation of up to 1,000 ppm dichloroethylene resulted in no identified ill effects in rats, rabbits, guinea pigs, and dogs [ACGIH 1991; Hathaway et al. 1991]. Dogs narcotized by inhaling 1,2-dichloroethylene vapor developed superficial corneal turbidity that cleared within 48 hours and did not disturb vision [Grant 1986].

2. Effects on Humans: The major effect of 1,2-dichloroethylene is narcosis; it has been used in a combination with ether (Dichloren) as an anesthetic in at least 2000 cases. No evidence of eye toxicity was seen in these cases [Grant 1986]. In high concentrations, exposure to 1,2-dichloroethylene causes central nervous system depression; in milder exposures, it can produce nausea, vomiting, weakness, tremor, epigastric cramps, burning of the eyes and vertigo [Gosselin 1984; Hathaway et al. 1991]. One fatality has been reported that was due to inhalation of a very high vapor concentration in a small enclosure [Hathaway et al. 1991].

* Signs and symptoms of exposure

1. Acute exposure: Exposure to the vapor of dichloroethylene may cause burning of the eyes. Other symptoms of acute exposure are nausea, vomiting, and epigastric distress. Symptoms of exposure-related narcosis including drowsiness, tremor, incoordination, dizziness, and weakness; these symptoms clear quickly after exposure is terminated.

2. Chronic exposure: 1,2-Dichloroethylene is a defatting agent, and repeated skin exposure may cause irritation and dermatitis.

EMERGENCY MEDICAL PROCEDURES

* Emergency medical procedures: [NIOSH to supply]

5. 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 1,2-dichloroethylene and lead to worker exposures to this substance:

* The manufacture and transportation of 1,2-dichloroethylene

* Use as a low-temperature extraction solvent for heat-sensitive substances (caffeine, perfume oils, and fats from fish and meat) and in dye extraction.

* Use as a general solvent of gums, rubber, waxes, oils, camphor, phenol, esters, ether derivatives, acetyl cellulose, lacquers, resins, thermoplastics, artificial fibers, and organic materials.

* Use as a chemical intermediate in the synthesis of polymers, telomers, and chlorinated solvents and compounds.

* Use in miscellaneous applications as dry cleaning agent, cleaning solution for printed circuit boards, food packaging adhesives, germicidal fumigants, and in retarding fermentation.

* Use as a refrigerant and coolant and in the manufacture of artificial pearls and pharmaceuticals.

Methods that are effective in controlling worker exposures to 1,2-dichloroethylene, 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 1,2-dichloroethylene 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 1,2-dichloroethylene, 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 skin, respiratory system, liver, and kidneys. 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 1,2-dichloroethylene 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 skin, respiratory system, liver, or kidneys.

* 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 1,2-dichloroethylene exposure. The interviews, examinations, and medical screening tests should focus on identifying the adverse effects of 1,2-dichloroethylene on the skin, respiratory system, liver, or kidneys. 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.

* 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 1,2-dichloroethylene.

WORKPLACE MONITORING AND MEASUREMENT

Determination of a worker's exposure to airborne 1,2-dichloroethylene is made using a charcoal tube (100/50 mg sections, 20/40 mesh). Samples are collected at a maximum flow rate of 0.2 liter/minute until a maximum collection volume of 5 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 described in the OSHA Computerized Information System [OSHA 1994] and is fully validated. NIOSH has published this method (Method No. 1003) in the NIOSH Manual of Analytical Methods [NIOSH 1994b].

PERSONAL HYGIENE PROCEDURES

If 1,2-dichloroethylene contacts the skin, workers should immediately wash the affected areas with large amounts of soap and water.

Clothing contaminated with 1,2-dichloroethylene 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 1,2-dichloroethylene, particularly its potential for causing irritation and at high concentrations, narcotic effects.

A worker who handles 1,2-dichloroethylene 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 1,2-dichloroethylene or a solution containing 1,2-dichloroethylene is handled, processed, or stored.

STORAGE

1,2-Dichloroethylene 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 1,2-dichloroethylene should be protected from physical damage and should be stored separately from strong oxidizers, strong alkalies, potassium hydroxide, or copper.

SPILLS AND LEAKS

In the event of a spill or leak involving 1,2-dichloroethylene, 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. Do not touch the spilled material; stop the leak if it is possible to do so without risk.

2. Notify safety personnel.

3. Remove all sources of heat and ignition.

4. Ventilate the area of the spill or leak.

5. Use non-sparking tools.

6. Use water spray to reduce vapors; do not get water inside the container.

7. Keep spilled material out of confined spaces because of the possibility of explosions.

8. For small liquid spills, take up with sand or other noncombustible absorbent material and place into closed containers for later disposal.

9. For large liquid spills, build dikes far ahead of the spill to contain the 1,2-dichloroethylene for later reclamation or disposal.

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

1,2-dichloroethylene 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].

Employers are not required by the emergency release notification provisions in 40 CFR Part 355.40 to notify the National Response Center of an accidental release of 1,2-dichloroethylene; there is no reportable quantity for this substance.

* 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 1,2-dichloroethylene per calendar year or otherwise use 10,000 pounds or more of 1,2-dichloroethylene 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 1,2-dichloroethylene 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 1,2-dichloroethylene 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 1,2-dichloroethylene 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 1,2-dichloroethylene. 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 1,2-dichloroethylene. The resistance of various materials to permeation by 1,2-dichloroethylene is shown below:

(*) Not recommended, degradation may occur

To evaluate the use of these materials with 1,2-dichloroethylene, 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 1,2-dichloroethylene.

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.

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