POLYCHLORINATED BIPHENYLS (PCB's) - Environmental Implications

Polychlorinated Biphenyls (PCB's) - An Introduction

Polychlorinated Biphenyls (PCB’s) are a range of substances consisting of a biphenyl molecule with or without alkyl or aryl substituents, in which more than one chlorine atom is substituted in the biphenyl nucleus. It is believed that PCB’s do not occur naturally. They are resistant to chemical and biochemical process. PCB’s are excellent dielectrics, stable to thermal, chemical and biological degradation and are fire resistant. These have been in use commercially, since 1930 as dielectric and heat exchange fluids and in a variety of other applications. Their thermal stability, chemical stability e.g. general inertness to oxidation and hydrolysis and dielectric properties have made these very useful in a variety of industrial applications. PCB’s were developed as high boiling point stable, heat-transfer fluids for use in transformers and heat exchangers. Other major uses of PCB’s included hydraulic fluids, plasticizers, carbonless carbon paper, inks, lubricants, waxes, cutting oils, and adhesives. They have been used as coolant – insulation fluids in capacitors and transformers, as agents for impregnating cotton and asbestos, in braided insulation of electrical wiring; as high – pressure hydraulic fluids; as heat transfer agents (Gustafson, 1970). In United States of America approximately 50% of total production was used in capacitors and transformers and 20% as plasticizers between 1930 to 1970. The degree of chlorination of PCB’s being adjusted according to the intended use.

The PCB’s had been discovered before the turn of 19th century and were first produced in 1929 as Aroclor. The bulk of commercial Aroclors consists of about 50 PCB’s isomers. The commercial mixtures of PCB’s in term of Aroclor is designated by four digit numbers of which the first pair (e.g. 12 in Aroclor 1242) designate the category of PCB’s and the second pair of digits designate the approximate percentage of chlorine, e.g. Aroclor 1242 has 42% chlorine, equivalent to the composition C12H7Cl3 and is a liquid with a boiling point of 380C, while Aroclor 1260 is 60% Chlorine, equivalent to C12H4Cl6 and is a solid. PCB’s are very resistant to chemical and bio-chemical degradation, their stability increases with the degree of chlorination and therefore they persist in the environment. Individual PCB isomers can differ sharply in their persistence, with the monochlorinated compounds generally being quite biodegradable. PCB’s with three or more chlorines on each phenyl rings are generally quite persistent, highly lipophilic (soluble to 10% in fat), water soluble, and extremely stable in the environment.

PCB’s are widely distributed in the environment throughout the world, and are persistent and accumulative in food web. Polychlorinated biphenyls have been found in environmental and biological samples at many locations and tend to accumulate in sediments, soils and biota (Pal et.al., 1980). The widespread distribution of PCB’s has been attributed to their volatilization or aerosol formation and atmospheric transport followed by wet or dry deposition.

PCB’s are practically insoluble in water, whereas they dissolve easily in hydrocarbons, fats and other organic compounds and they are readily absorbed by fatty tissues. The risk of human exposure to PCB’s had been excessively large due to their persistent nature and have resulted due to the consumption of contaminated food, as well as from inhalation and skin absorption in work environment. PCB’s accumulated in the fatty tissues of humans and other animals are the cause of toxic effects. The skin and liver are the major sites of PCB’s cytological effects, but the gastrointestinal tract, the immune system and the nervous system are also the major targets.