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Table of Contents
 
Summary
Industry Overview
Recent and Future Trends
Manufacturing Processes
PCE and/or TCE by Chlorination of C2 Chlorinated Hydrocarbons
PCE and/or TCE by Oxychlorination of C2 Chlorinated Hydrocarbons
PCE and TCE by Chlorination of Ethylene and Thermal Dehydrochlorination of Product
PCE (and CCl4) by Chlorination of C1-C3 Hydrocarbons or Their Partially Chlorinated Derivatives
PCE and TCE by Chlorination of Acetylene
1,1,1-TCA from EDC via Vinyl Chloride
1,1,1-TCA from EDC via 1,1,2-Trichloroethane
1,1,1-TCA by Chlorination of Ethane
Stabilization
Environmental Issues and Regulations
Regulations Governing Occupational Exposure
United States
Western Europe
Japan
Regulations Governing Atmospheric Pollution
United States
Perchloroethylene and Trichloroethylene
Dry cleaning
Metal degreasing
1,1,1-TCA
Canada
Western Europe
Japan
Other U.S. Regulations Affecting C2 Chlorinated Solvents
The Montreal Protocol
Ozone-Depletion and the Montreal Protocol
Climate Change and Global Warming
Impact on Fluorocarbons
United States
Phaseout schedule
Reclamation and reuse
Europe
Japan
Developing Countries
Supply and Demand by Region
United States
Producing Companies
Production
Salient Statistics
Perchloroethylene
Trichloroethylene
1,1,1-Trichloroethane
Consumption
Perchloroethylene
Chemical intermediates (precursor)
Metal cleaning
Dry cleaning and textile processing
Other
Trichloroethylene
Chemical intermediates (precursor)
Metal cleaning
Other
1,1,1-Trichloroethane
Price
Trade
Imports
Exports
Canada
Consumption
Price
Trade
Imports
Exports
Mexico
Consumption
Price
Trade
Central and South America
Producing Companies
Salient Statistics
Perchloroethylene
Trichloroethylene
1,1,1-Trichloroethane
Consumption
Price
Trade
Imports
Perchloroethylene
Trichloroethylene
1,1,1-Trichloroethane
Exports
Western Europe
Producing Companies
Production
Salient Statistics
Perchloroethylene
Trichloroethylene
1,1,1-Trichloroethane
Consumption
Perchloroethylene
Dry cleaning
Chemical intermediates (precursor)
Trichloroethylene
Chemical intermediates (precursor)
Metal cleaning (vapor degreasing)
1,1,1-Trichloroethane
Chemical intermediates (precursor)
Metal cleaning and other uses
Price
Trade
Central and Eastern Europe
Producing Companies
Production
Salient Statistics
Perchloroethylene
Trichloroethylene
Consumption
Price
Trade
Imports
Perchloroethylene
Trichloroethylene
Exports
Perchloroethylene
Trichloroethylene
Africa and Middle east
Consumption
Price
Trade
Imports
Perchloroethylene
Trichloroethylene
Exports
Japan
Producing Companies
Production
Consumption
Perchloroethylene
Trichloroethylene
1,1,1-Trichloroethane
Price
Trade
China
Producing Companies
Production
Consumption
Price
Trade
Other Asia and Oceania
Producers
Production
Perchloroethylene
Trichloroethylene
Consumption
Perchloroethylene
Trichloroethylene
1,1,1-Trichloroethane
Price
Trade
Imports
Perchloroethylene
Trichloroethylene
1,1,1-Trichloroethane
Exports
Perchloroethylene
Trichloroethylene
1,1,1-Trichloroethane
   
  C2 Chlorinated Solvents
   
  James Glauser with Yosuke Ishikawa
  Published August 2008
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  Abstract
   
 

The C2 chlorinated solvents that have major commercial significance are perchloroethylene (PCE), trichloroethylene (TCE), and 1,1,1-trichloroethane or methyl chloroform (TCA). Consumption of these solvents has been negatively impacted by declines in emissive applications as a result of regulations related to the 1987 Montreal Protocol on ozone depleting chemicals and the 1997 Kyoto Protocol on global warming and climate change. Use of TCA has been phased out in most countries because of its ozone depletion potential (ODP) in the upper atmosphere. Consequently, global consumption of all three solvents is primarily for use as a feedstock in the production of fluorocarbons.

Over the past two decades, the global fluorocarbons market has undergone a number of major transitions toward a greater use of non-ozone-depleting HFCs and non-global-warming, nonfluorocarbon alternatives in emissive applications. Consumption in the largest market segment, refrigeration and air-conditioning, was negatively impacted by both Montreal and Kyoto Protocol amendments and legislation and there are current and proposed regulations limiting the future production, consumption and trade of CFCs, HCFCs and HFCs.

The following chart shows world production and consumption of the three major C2 chlorinated solvents as a percentage of the world total:

Global consumption of C2 chlorinated solvents has decreased significantly for emissive uses (e.g., dry cleaning and metal cleaning) in the last twenty years. Governments in all major industrialized regions have set strict standards limiting the exposure of workers and the environment to these potentially hazardous compounds. The presence of chlorinated solvents in groundwater remains problematic. Furthermore, 1,1,1-TCA is considered an ozone depleter and its use for emissive applications has been almost totally banned around the world. It is still being used as an intermediate in the production of fluorocarbons, pharmaceuticals and other small applications.

Currently, the largest use for all three C2 chlorinated solvents is as feedstocks for fluorocarbons. PCE has historically been used to make the chlorofluorocarbons CFC-113, CFC-114 and CFC-115. This end use has almost totally disappeared, as emissive uses of these materials have been banned in most countries because of their contribution to ozone depletion. In the United States both PCE and TCE are used to make hydrofluorocarbon-134a (HFC-134a), which is the most popular alternative to CFC-12 refrigerant in car air-conditioning systems. Lesser quantities of PCE and TCE are used for production of HCFC-123, HCFC-124 and HFC-125. PCE is used in Japan to produce HFC-134a, while TCE is used in Western Europe. HFC-125 consumption is growing as a replacement for HFC-134a, which will be banned in Europe after 2017.

1,1,1-TCA is used principally to make HCFC-141b and HCFC-142b, and HFC-143a. Countries like China and India have agreed to cease use of 1,1,1-TCA and CFCs no later than 2010. China phased out CFCs in 2008, and remains ahead of schedule. The use of 1,1,1-TCA was banned in the United States in 2003 for emissive uses.

 

 
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