Difference between revisions of "PCB"

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They have been contaminants in the marine environment for more than 60 years. In this time they have become universally distributed in marine and [[estuarine]] environments. They occur in nearly all marine plant, [[pollution and algae|algae]] and animal species. Like other organochlorine compounds they are a hazard to marine ecosystems because of their extreme stability, low biodegradability and lipid solubility, which causes them to [[bioaccumulation|bioaccumulate]]. Concentrations of PCBs in surface waters vary between 0,035 n/l (in open ocean), to 10 ng/l in highly polluted coastal waters. However, decreasing trends are being observed since concentrations peaked in the 1970s. <ref name = pub> Kennish, M. J. (1996): Practical Handbook of Estuarine and Marine Pollution, CRC Press 524 pp</ref>
 
They have been contaminants in the marine environment for more than 60 years. In this time they have become universally distributed in marine and [[estuarine]] environments. They occur in nearly all marine plant, [[pollution and algae|algae]] and animal species. Like other organochlorine compounds they are a hazard to marine ecosystems because of their extreme stability, low biodegradability and lipid solubility, which causes them to [[bioaccumulation|bioaccumulate]]. Concentrations of PCBs in surface waters vary between 0,035 n/l (in open ocean), to 10 ng/l in highly polluted coastal waters. However, decreasing trends are being observed since concentrations peaked in the 1970s. <ref name = pub> Kennish, M. J. (1996): Practical Handbook of Estuarine and Marine Pollution, CRC Press 524 pp</ref>
 
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PCBs have been shown to cause reproductive abnormalities in [[Pollution and marine mammals|marine mammals]] and chronic diseases in [[Pollution and humans|humans]] (such as skin lesions, reproductive disorders and liver damage). Furthermore they are suspected to be carcinogenic. They also tend to act as [[endocrine disrupting compounds]]. Concentrations which (in laboratory conditions) cause lethal effects in fish range from 10 ppm to 300ppm. The concentrations measured in the 1970s in wild fishes and seal varied between 0,03 and 212 ppm.<ref name = pub> Kennish, M. J. (1996): Practical Handbook of Estuarine and Marine Pollution, CRC Press 524 pp</ref>
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PCBs have been shown to cause reproductive abnormalities in [[Pollution and marine mammals|marine mammals]] and chronic diseases in [[Pollution and humans|humans]] (such as skin lesions, reproductive disorders and liver damage). Furthermore they are suspected to be carcinogenic. They also tend to act as [[endocrine disrupting compounds]], which disrupt the hormone balance of animals. This might cause [[immunodeficiency]] and or reproductive problems. These effects are suspected to occur at much lower concentrations than those which cause acute toxicity.<ref>OSPAR Commission 2000. Quality Status Report 2000, OSPAR Commission, London</ref> Concentrations which (in laboratory conditions) cause lethal effects in fish range from 10 ppm to 300ppm. The concentrations measured in the 1970s in wild fishes and seal varied between 0,03 and 212 ppm.<ref name = pub> Kennish, M. J. (1996): Practical Handbook of Estuarine and Marine Pollution, CRC Press 524 pp</ref>
 
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Revision as of 14:02, 24 July 2009

Definition of PCB:
Polychrorinated biphenyls (PCBs) is a large group of toxic synthetic lipid-soluble chlorinated hydrocarbons, which are used in various industrial processes and which have become persistent and ubiquitous environmental contaminants which can be concentrated in food chains.[1]
This is the common definition for PCB, other definitions can be discussed in the article

Notes

Between the time of initial (1929) and final production (1977) the USA produced an estimated 0,54 billion kg of PCB's. They were widely used in transformers and capacitors, lubricants, fire retardants, plastics and other materials. PCBs can enter the marine environment by adsorption to particles and atmospheric transport. [2]

They have been contaminants in the marine environment for more than 60 years. In this time they have become universally distributed in marine and estuarine environments. They occur in nearly all marine plant, algae and animal species. Like other organochlorine compounds they are a hazard to marine ecosystems because of their extreme stability, low biodegradability and lipid solubility, which causes them to bioaccumulate. Concentrations of PCBs in surface waters vary between 0,035 n/l (in open ocean), to 10 ng/l in highly polluted coastal waters. However, decreasing trends are being observed since concentrations peaked in the 1970s. [3]

PCBs have been shown to cause reproductive abnormalities in marine mammals and chronic diseases in humans (such as skin lesions, reproductive disorders and liver damage). Furthermore they are suspected to be carcinogenic. They also tend to act as endocrine disrupting compounds, which disrupt the hormone balance of animals. This might cause immunodeficiency and or reproductive problems. These effects are suspected to occur at much lower concentrations than those which cause acute toxicity.[4] Concentrations which (in laboratory conditions) cause lethal effects in fish range from 10 ppm to 300ppm. The concentrations measured in the 1970s in wild fishes and seal varied between 0,03 and 212 ppm.[3]

There are 209 different forms of PCBs. Therefore, to asses the risk of PCB exposure, the sum of all these forms needs to be taken into account. [3]

See also

PCB and heavy metals in beached sperm whales

Pesticides in harbour porpoises

The relation between pollutants and disease in guillemots

Effects of xenoestogens in eels

PCBs and organochlorine pesticides in Antarctic algae

Levels of PCBs and organochlorine pesticides in various benthic species in the Belgian North sea and the Western Scheldt estuary

PCBs and organochlorine pesticides in shrimp from the Belgian North Sea

References

  1. Lawrence E (ed.), 2000. Henderson’s Dictionary of Biological Terms. 12th edition. Prentice Hall, Pearson Education Limited. Harlow, Great Britain.
  2. Clark, R,B., 1999. Marine pollution. Oxford University press, Fourth edition, pp 161
  3. 3.0 3.1 3.2 Kennish, M. J. (1996): Practical Handbook of Estuarine and Marine Pollution, CRC Press 524 pp
  4. OSPAR Commission 2000. Quality Status Report 2000, OSPAR Commission, London