VINYL CHLORIDE

Ackroyd, Lyndsey 

Asfour, Omar

Banks, Dan

Wolfe, Natalie

CHEMISTRY AND RELATED PROPERTIES

Vinyl Chloride (at room temperature) is a flammable, colorless gas with a sweet odor. It is used in the plastics industry, often to produce PVC (polyvinyl chloride). It is also used as a refrigerant, and in organic synthesis reactions. It may be prepared by halogenation with ethylene dichloride and alcoholic potassium.

Chemical Formula: C2H3Cl
Alternate Name: chloroethene, chloroethylene, ethylene monochloride
Structure:
Molecular Weight: 62.50 g/mol
Melting / Boiling Point: -153.8° C / -13.37° C
Density: (21.1° C and 1 atm) à 2.56 kg/m3 (Gas)
à 908.41 kg/m3 (Liquid)
Solubility (in Water): Slight (8800 mg/L) @ 25° C
(High Solubility in Alcohol, Ether, carbon tetrachloride, benzene)
Henry’s Law Contant: 0.0278 atm.m3/mde@ 24° C
Octanol:Water: logKow 1.62 [Kow 41.7 (Calculated)]
Soil Partition Coefficient (Koc): 56 (estimated)
Vapour Pressure: 2530 mm Hg @ 20° C
Flash Point: -78° C (-112° F)
Emmission Limit: 10ppm or 2kg/day (Process Vent)

DETECTION IN AIR
Gas Chromatography may be used for a range of 0.008 to 5.2 mg/m3 using flame ionization detection. For qualitative detection, we may use a Drager detector tube for vinyl chloride. A change in color from from violet to pale brown indicates the presence of vinyl chloride.

DETECTION IN WATER
For a range of 40 to 400 ppm, presence may be determined by partition infrared spectrophotometry. Qualitative detection may be facilitated by infrared spectroscopy. (Environment Canada, 1992)

MANUFACTURE, QUANTITY AND DISTRIBUTION

Vinyl chloride is most commonly made by the "balanced process" in which ethylene is reacted to produce ethylene dichloride, which in turn is dehydrochlorinated to produce vinyl chloride. The raw materials used in the manufacture of vinyl chloride are ethylene and hydrogen chloride.

Ethylene is reacted with hydrogen chloride and oxygen to produce ethylene dichloride. The reaction is usually carried out in the vapour phase over catalysts containing copper chloride as the active catalyst. The overall reaction is as follows:

CH2=CH2 + 2HCl + ½ O2 à ClCH2CH2Cl + H20

The ethylene dichloride is purified to remove any FeCl3 (which poisons catalysts in the next phase) and is reacted at 2500-3000 kPa at temperatures of 425-550oC to yield vinyl chloride and hydrogen chloride. The hydrogen chloride is recycled to the first step (thus the name "balanced process" for this entire procedure).

ClCH2CH2Cl à CH2=CHCl + HCl

The resulting vinyl chloride is purified by distillation to remove the byproducts (unreacted material, chlorinated hydrocarbons, hydrocarbons). This vinyl chloride monomer (VCM) is combined with an agent called an initiator which start the reaction that produces a fine-grained, white powder known as polyvinyl chloride (PVC) resin, or simply "vinyl".

Quantities Produced and Geographic Distribution

Canadian producers of vinyl chloride and PVC:

Company Location Product
Dow Chemical Canada Inc. Sarnia, Ontario Vinyl chloride
Dow Chemical Canada Inc. Fort Saskatchewan, Alberta Vinyl chloride
B.F. Goodrich Canada Inc. Niagara Falls, Ontario Polyvinyl chloride
B.F. Goodrich Canada Inc. Fort Saskatchewan, Alberta Polyvinyl chloride
Esso Chemicals Canada Sarnia, Ontario Polyvinyl chloride

Fate of Vinyl Chloride After Use

Most of the vinyl chloride that enters the environment comes from the plastics industries, which release it into the air or into waste water. Vinyl chloride has entered the environment at hazardous waste sites as a result of its improper disposal or leakage from storage or transport containers or from spills.

Vinyl chloride is shipped as a liquefied compressed gas. It has a boiling point of –13.4oC at a pressure of 1 atmosphere. Consequently, when it is spilled onto soil extensive evaporation will occur. While most will be lost to evaporation, the balance will infiltrate the soil. Evaporation will continue within the soil but at a reduced rate.

When spilled on water, some of the material will dissolve, and the rest will evaporate to the atmosphere. Vinyl chloride spills on soil surfaces will partly vaporize, and partly adsorb onto the soil at a rate dependent on the soil type and its degree of saturation with water. Downward transport of the liquid toward the groundwater table may cause environmental concerns.

General Source Assessment

Vinyl chloride is not normally found in urban, suburban, or rural air in amounts that are detectable by the usual methods of analysis. However, vinyl chloride has been found in the air near plastics industries, hazardous waste sites, and landfills. The amount of vinyl chloride in the air near these places ranges from trace amounts to 0.041 ppm of air, but may exceed 1 ppm.

Vinyl chloride can also be found in drinking water from contaminated wells, but how often this occurs is not known. Most drinking water supplies do not contain vinyl chloride. In a 1982 survey, vinyl chloride was found in less than 1 percent of the 945 groundwater supplies tested in the United States. The concentrations found in groundwater were up to 0.008 ppm, with a detection limit of 0.001 ppm. Other studies have reported groundwater vinyl chloride concentrations at or below 0.38 ppm.

Vinyl chloride has been found in at least 133 of 1177 hazardous waste sites on the National Priorities List (NPL) in the U.S. It is unlikely that vinyl chloride will build up in plants or animals that one might eat.

BIODEGRADATION

When in water, vinyl chloride does not appear to be sorbed, degraded or affected at all by microorganisms (experimentation included both bacterial and fungal populations). Chemical degradation is also insignificant in water. Vinyl chloride evaporates rapidly, and its half life in water at a depth of 1m is estimated to be 26 minutes. In air, vinyl chloride will be photodegraded to hydrogen chloride or formyl chloride, which in turn reacts to produce carbon monoxide and hydrogen chloride. The half life in air is estimated to be approximately 2 days.

SPILL CONTROL

SOIL SPILL

Construct barriers and pump out liquid; if this is unsafe, let evaporate


WATER SPILL

Limit spreading by using natural barriers or booms. Activated carbon can be applied at 10 percent the spill amount over the region occupied by 10mg/L or greater concentrations - mechanical dredges can then be used to remove the carbon, aeration of contaminated water will also substantially remove the contaminant


PROTECTION REQUIRED WHEN DEALING WITH A SPILL

ENVIRONMENTAL PATHWAYS

HEALTH EFFECTS

ACUTE (SHORT TERM) EXPOSURE


CHRONIC (LONG TERM) EXPOSURE


 

 

References

  1. Budavari, S. et al. The Merck Index (12th ed.). Merck Research Laboratories, Whitehouse Station NJ, 1996. pp. 1705-6.
  2. Environment Canada. Vinyl Chloride Industry Environmental Status Report (1987-90). Environment Canada, Ottawa, 1992. pp. 2, 73-75.
  3. http://www.atsdr.cdc.gov/ToxProfiles/phs8825.html (October 14, 2000)
  4. http://physchem.ox.ac.uk/MSDS/V/vinyl_chloride.html (September 22, 2000)
  5. http://ceh.sric.sri.com/Public/Reports/696.6000/ (October 14, 2000)
  6. http://www.usadata.com/cgi-bin/usasearch.cgi (October 14, 2000)
  7. http://www.vinylinfo.org/materialvinyl/process.html (October 14, 2000)
  8. http://esc.syrres.com/interkow/webprop.exe?CAS=75-01-4 (October 14, 2000)