Polychlorinated Biphenyls

Polychlorinated biphenyls are a family of man-made chemicals that contain two
hundred and nine individual compounds with varying toxicity. Many different
combinations are possible. In chemical terminology, "phenyl" denotes a ring
structure of six carbon atoms attached to something else; "biphenyl" results
when two such rings are attached to each other. Polychlorinated biphenyl (PCB)
is any molecule having multiple chlorine atoms attached to the carbon atoms of a
biphenyl nucleus. Chlorine atoms can be placed at any or all of ten available
sites. PCBs have been used widely as coolants and lubricants in transformers,
capacitors, and other electrical equipment. The manufacture of PCBs stopped in
the United States in October 1977 because of evidence that PCBs accumulate in
the environment and may cause health hazards for humans. Although PCBs are no
longer manufactured, human exposure still occurs. Many older transformers and
capacitors still contain fluids that contain PCBs. The useful lifetime of these
transformers can be thirty years or more. Prior to 1977, certain occupational
settings had, and may still have, higher levels of human exposure. Animal
experiments have shown that some PCB mixtures produce adverse health effects
that include liver damage, skin irritations, reproductive and developmental
effects, and cancer. With these observations, it is most considerably dangerous
for humans. The U.S Department of Health and Human Services has determined that

PCBs may reasonably be expected to be carcinogens. Human studies to date show
that irritations, such as acne-like lesions and rashes, can occur in PCB-exposed
workers. Other studies of people with occupational exposure suggest that PCBs
might cause liver cancer. Reproductive and developmental effects may also be
related to occupational exposure and eating of contaminated fish. While the role
in producing cancer, reproductive and developmental effects can not be clearly
determined, the suggestive evidence provides an additional basis for public
health concerns about humans who might be exposed to PCBs. It has also been
suggested that chemicals such as PCBs in the environment can mimic the bodys
natural hormones. This could lead to infertility, certain types of cancer, and
other hormone-related disorders. In the past, discharges of PCB-filled wastes
into rivers, streams and open landfills were considered acceptable, legal and
hazard-free practices. PCBs were also sometimes intentionally released into the
environment to reduce dust emissions from dirt roads, or as extenders in some
agricultural pesticides formulations. These practices were inappropriate and
potentially harmful. There have also been accidental releases of PCB and
associated contaminants into the environment via leaking of sealed PCB fluid
compartments during commercial use of transformers and capacitors, as a result
of improper disposal of PCB-containing equipment or chemical products. The
contamination of food for animal and human consumption has also occurred from

PCBs leaking from malfunctioning heating coils into foods during manufacturing.

PCBs can also enter the food chain through the ingestion of contaminated fish
from PCB-contaminated water. Finally, transformer and capacitor fires have led
to the environmental release of PCBs and thermal degradation products. Concern
about the presence of PCBs in our environment began around 1966 when research in

Sweden revealed the presence of PCBs in environmental samples being screened for

DDT. Further study confirmed suspicions that the rate of natural breakdown was
very slow for some of the PCB congeners. Concern continued to rise due to
widespread human poisoning episodes in 1968 and 1978. PCBs are now regarded as
environmental contaminants that build up in the food chain. They build up in the
food chain due to their relative insolubility in water and high solubility in
fats. To date, there are tests to determine PCBs in blood, body fat and breast
milk. These tests are not routine clinical tests, but they can detect PCBs in
members of the general population as well as in workers with occupational
exposure to PCBs. Although these tests indicate if one has been exposed to PCBs,
they do not predict potential health effects. Blood tests are the easiest,
safest and perhaps, the best method for detecting recent large exposures. As
well as tests, remediation techniques and disposal technologies continue to
evolve. Many approaches have been tested out but none has emerged as a
technically and economically viable solution for the endless environmental
situations encountered. A useful method for cleansing water will probably not be
effective in treating soil. Highly chlorinated PCBs will not be as readily
decomposed as less-chlorinated PCBs. These types of factors contribute to the
challenge of effective and cost-efficient remediation of PCB contaminated sites.

Bacterial build-up or breakdown of PCBs in soil and sediment is potentially
useful technology that is receiving much attention. Introductory results on the
breakdown of soil samples, including those taken from the