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Effects on Human Health
The greatest part of human exposure to the 12 POPs is attributed to the
ingestion of food. Contamination of food may occur through environmental
pollution in the air, water and soil, or through the previous use or unauthorised
use of organochlorine
pesticides
on food crops. Food rich in animal fat, such as meats, fish, and dairy
products are the most important means of exposure often due to bioaccumulation
through the food chain.
For some POPs, occupational and accidental high-level exposure, through
inhalation and dermal contact, is of concern for both acute and chronic
worker exposure. In addition to other exposure routes, worker exposure
to POPs during waste management is a significant source of occupational
risk in many countries. Short-term exposure to high concentrations of
certain POPs has been shown to result in illness and death.
The health effects of POPs are generally subtle and can be triggered
at extraordinary low concentrations. The latency period for POPs may be
very long. Not only can there be may years between exposure and outcome
in the exposed individual, but in some cases effects occur in future generations.
(WFPHA, World Federation of Public Health Associations, 2000).
Exposure to POPs can be associated with the following health effects
in humans:
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Immune system biochemical alterations;
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Reproductive deficits;
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A shortened period of lactation in nursing mothers;
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Neurobehavioral impairment including learning disorders, reduced
performance on standard tests, and attention deficits;
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Diabetes;
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Cancer.
The following table shows the evaluation of carcinogenic risk to humans
for the 12 POPs made by IARC, International Agency for Research on Cancer.
| IARC (International
Agency for Research on Cancer) Classification |
POPs |
| Group 1: The agent (mixture) is carcinogenic
to humans |
2,3,7,8-Tetrachlorodibenzo-para-dioxin (TCDD) |
| Group 2A: The agent (mixture) is probably carcinogenic
to humans |
Mixtures of polychlorinated biphenyls |
| Group 2B: The agent (mixture) is possibly carcinogenic
to humans |
Chlordane
DDT
Heptachlor
Hexachlorobenzene
Mirex
Toxaphene (mixtures of Polychlorinated camphenes)
|
| Group 3: The agent (mixture or exposure circumstance)
is unclassifiable as to carcinogenicity in humans |
Aldrin
Dieldrin
Endrin
Polychlorinated dibenzo-para-dioxins (other than TCDD)
Polychlorinated dibenzofurans |
It is possible to document three distinct types of human exposure to
POPs.
-
High-dose acute exposure: typically results from accidental
fires or explosions involving electrical capacitors or other PCB-containing
equipment, or high dose food contamination.
-
Mid-level chronic exposure is predominantly due to the occupational
exposure, and , in some cases, also due to the proximity of environmental
storage sites or high consumption of a POPs-contaminated dietary source,
such as fish or other marine animals.
-
Chronic, low-dose exposure is characteristic for the general
population world-wide as a consequence of the existing global background
levels of POPs with a variations due to diet, geography, and level
of industrial pollution. Low level and population-wide effects are
more difficult to study. People are exposed to multiple POPs during
their lifetime and most people today carry detectable levels of a
number of POPs in their body. (WFPHA, 2000).
Find More Sources On POPs and Health Effects
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Case
study of POPs concentrations in wildlife and people relative to effects
levels. (htm file)
Dr. D. Stone, Chief, Environmental Services and Research Division,
Hull, Quebec, Canada. Proceedings of the subregional Awareness Raising
Workshop on Persistent Organic Pollutants (POPs), Bangkok, Thailand,
25-28 November 1997. |
|
Health
Effects of POPs. (htm file). Dr. J. Stober, Executive Secretary
of IFCS, Switzerland. Proceedings of the subregional Awareness Raising
workshop on Persistent Organic Pollutants (POPs), Kranjska Gora,
Slovenia, 11-14 May 1998.
|
Communicating
information concerning POPs exposure and risks to an arctic population.
(htm file)
Dr. D. Stone, Chief, Environmental Services and Research Division,
Hull, Quebec, Canada. Proceedings of the subregional Awareness Raising
Workshop on Persistent Organic Pollutants (POPs), Bangkok, Thailand,
25-28 November 1997. |
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IARC criteria
for evaluating the strength of the evidence for carcinogenicity.
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