Difference between revisions of "Persistent organic pollutant"

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Public concern about persistent organic pollutants was first raised in the early 1960s with the publication of the book ''Silent Spring'' (1962) by U.S. author Rachel Carson (1907–64), which led to the banning of [[DDT]] for agricultural use in the United States in 1972. The U.S. and several other countries have regulated POPs on a case-by-case basis since then. A more systematic approach to the regulation of POP production and use can be found in the [[Stockholm Convention on Persistent Organic Pollutants]], signed in 2001, and the European Union [[REACH Regulation]] (1907/2006).<ref name="REACH">[http://eur-lex.europa.eu/LexUriServ/LexUriServ.do?uri=OJ:L:2006:396:0001:0849:EN:PDF Regulation (EC) No 1907/2006 of the European Parliament and of the Council of 18 December 2006 concerning the Registration, Evaluation, Authorisation and Restriction of Chemicals (REACH), establishing a European Chemicals Agency, amending Directive 1999/45/EC and repealing Council Regulation (EEC) No&nbsp;793/93 and Commission Regulation (EC) No&nbsp;1488/94 as well as Council Directive 76/769/EEC and Commission Directives 91/155/EEC, 93/67/EEC, 93/105/EC and 2000/21/EC], ''OJEU'' L396, 30.12.2006, pp&nbsp;1–849.</ref>
 
Public concern about persistent organic pollutants was first raised in the early 1960s with the publication of the book ''Silent Spring'' (1962) by U.S. author Rachel Carson (1907–64), which led to the banning of [[DDT]] for agricultural use in the United States in 1972. The U.S. and several other countries have regulated POPs on a case-by-case basis since then. A more systematic approach to the regulation of POP production and use can be found in the [[Stockholm Convention on Persistent Organic Pollutants]], signed in 2001, and the European Union [[REACH Regulation]] (1907/2006).<ref name="REACH">[http://eur-lex.europa.eu/LexUriServ/LexUriServ.do?uri=OJ:L:2006:396:0001:0849:EN:PDF Regulation (EC) No 1907/2006 of the European Parliament and of the Council of 18 December 2006 concerning the Registration, Evaluation, Authorisation and Restriction of Chemicals (REACH), establishing a European Chemicals Agency, amending Directive 1999/45/EC and repealing Council Regulation (EEC) No&nbsp;793/93 and Commission Regulation (EC) No&nbsp;1488/94 as well as Council Directive 76/769/EEC and Commission Directives 91/155/EEC, 93/67/EEC, 93/105/EC and 2000/21/EC], ''OJEU'' L396, 30.12.2006, pp&nbsp;1–849.</ref>
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Initial concern over persistent organic pollutants centred on [[organochlorine insecticide]]s, industrial [[organochlorine compound]]s such as [[polychlorinated biphenyls]] (PCBs) and byproducts such as [[dioxins]]. Other classes of POPs include [[organobromine compound|brominated]] [[flame retardant]]s, [[Organofluorine compound|perfluorooctyl compounds]] and [[nitro compound]]s such as [[musk xylene]].
  
 
==Definitions==
 
==Definitions==

Revision as of 10:04, 21 December 2009

A persistent organic pollutant (POP) is an organic compound that is only slowly degraded in the environment, so that it tends to persist and even to accumulate rather than being broken down by photochemical or biological processes. Accumulation can occur either in the environment (eg, in sediments) or in the tissue of animal or plant species (bioaccumulation).

Public concern about persistent organic pollutants was first raised in the early 1960s with the publication of the book Silent Spring (1962) by U.S. author Rachel Carson (1907–64), which led to the banning of DDT for agricultural use in the United States in 1972. The U.S. and several other countries have regulated POPs on a case-by-case basis since then. A more systematic approach to the regulation of POP production and use can be found in the Stockholm Convention on Persistent Organic Pollutants, signed in 2001, and the European Union REACH Regulation (1907/2006).[1]

Initial concern over persistent organic pollutants centred on organochlorine insecticides, industrial organochlorine compounds such as polychlorinated biphenyls (PCBs) and byproducts such as dioxins. Other classes of POPs include brominated flame retardants, perfluorooctyl compounds and nitro compounds such as musk xylene.

Definitions

A persistent organic pollutant could simply be defined in terms of its persistence in the environment, which would include substances such as crude oil. However, it is more normal also to take account of the potential for bioaccumulation and any toxicity associated with the substance. The Stockholm Convention Secretariat gives the following general definition:[2]

Persistent Organic Pollutants (POPs) are organic chemical substances, that is, they are carbon-based. They possess a particular combination of physical and chemical properties such that, once released into the environment, they:

  • remain intact for exceptionally long periods of time (many years);
  • become widely distributed throughout the environment as a result of natural processes involving soil, water and, most notably, air;
  • accumulate in the fatty tissue of living organisms including humans, and are found at higher concentrations at higher levels in the food chain; and
  • are toxic to both humans and wildlife.

The European Union distinguishes between PBT substances (persistent, bioaccumulative, toxic) and vPvB substances (very persistent, very bioaccumulative). All substances listed in the Stockholm Convention are vPvB under the EU classification, and also have evidence of toxicity and long-range environmental transport.

  Stockholm Convention[3] REACH Regulation[4][note 1]
Persistence
  • half-life in water > 2 months; or
  • half-life in soil > 6 months; or
  • half-life in sediment > 6 months.
P
  • half-life in marine water > 60 days; or
  • half-life in river or esturine water > 40 days; or
  • half-life in marine sediment > 180 days; or
  • half-life in river or esturine sediment > 120 days; or
  • half-life in soil > 120 days.
vP
  • half-life in water > 60 days; or
  • half-life in sediment > 180 days; or
  • half-life in soil > 180 days.
Bioaccumulation
  • bioconcentration factor for aquatic species > 5000; or
  • direct evidence of bioaccumulation in biota; or
  • other reasons for concern, such as high bioaccumulation in nonaquatic species, high toxicity or ecotoxicity.
  • In the absence of other data, log Kow > 5.
B bioconcentration factor for aquatic species > 2000.
vB bioconcentration factor for aquatic species > 5000.
Long-range environmental transport (LRET) evidence of LRET potential by air, water or migratory species, from either
  • measured concentrations distant from the source of pollution; or
  • modeling results.

For transport by air, the half-life in air should be > 2 days.

not taken into account
Toxicity evidence for the potential for damage to human health or to the environment, either direct or through laboratory studies.

Notes and references

Notes

  1. The modification to the REACH Regulation introduced by Art. 58.15 of the CLP Regulation will come into force on 1 December 2010: the original criteria were based on the Dangerous Substances Directive (67/546/EEC), but are almost identical to the new criteria.

References

External links

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