Difference between revisions of "Dibutylphthalate"

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{{Definition|title=dibutylphthalate (DBP)
 
{{Definition|title=dibutylphthalate (DBP)
  
|definition= Dibutylphthalate belongs to the family of phthalates: industrial chemicals used as plasticizers, softeners, adhesives or solvents used by a variety of industries. They are used in PVC, paints, printing inks, cosmetics, coatings of cars,... <ref name = OECD>[http://www.ospar.org/documents%5Cdbase%5Cpublications%5CP00270_BD%20on%20phthalates%20_2006%20version_.pdf OSPAR Commission, 2006: OSPAR background document on phthalates]</ref>}}
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|definition= Dibutylphthalate belongs to the family of phthalates: industrial chemicals used as plasticizers, softeners, adhesives or solvents used by a variety of industries. They are used in PVC, paints, printing inks, cosmetics, coatings of cars,...<ref name = OECD>[http://www.ospar.org/documents%5Cdbase%5Cpublications%5CP00270_BD%20on%20phthalates%20_2006%20version_.pdf OSPAR Commission, 2006: OSPAR background document on phthalates]</ref>.}}
  
 
== Notes ==
 
== Notes ==
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In 1998, 26.000 ton of dibutylphthalate was produced in the EU of which 18.000 ton was consumed in the EU. <P>
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In 1998, 26.000 tons of dibutylphthalate ware produced in the EU of which 18.000 ton was consumed in the EU. <P>
DBP can enter the marine environment through waste water effluents. Also cleaning of road tankers releases DBP in the aquatic environment. DBP has a low water solubility (10 mg/l), and tends to [[adsorption|adsorb]] to sediment. It is very stable but can be biodegraded, causing it to have an environmental [[half-life]] of 50 days. It has some potential to [[bioaccumulation|bioaccumulate]] in some organisms, however because of its biodegradability it is not expected to [[biomagnification|biomagnify]] through [[food chain|food chains]].  
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DBP can enter the marine environment through waste water effluents. Cleaning of road tankers releases DBP to the aquatic environment. DBP has a low water solubility (10 mg/l), and tends to [[adsorption|adsorb]] to sediments. It is very stable but can be biodegraded, causing it to have an environmental [[half-life]] of 50 days. It has some potential to [[bioaccumulation|bioaccumulate]] in some organisms, however because of its biodegradability it is not expected to [[biomagnification|biomagnify]] through [[food chain|food chains]]. <P>
Concentrations above 0,04 mg/l are shown to cause adverse effects on aquatic invertebrates and concentrations above 0,2 mg/l can have lethal effects. Concentrations above 0,5 mg/l can cause acute toxicity for fishes. It has also been show to be able to act as an [[endocrine disrupting compounds|endocrine disruptor]] in vertebrates. As such it could cause adverse effects on the development and reproduction of rats. <ref name = OECD>[http://www.ospar.org/documents%5Cdbase%5Cpublications%5CP00270_BD%20on%20phthalates%20_2006%20version_.pdf OSPAR Commission, 2006: OSPAR background document on phthalates]</ref><P>
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Concentrations above 0,04 mg/l are shown to cause adverse effects on aquatic invertebrates and concentrations above 0,2 mg/l can have lethal effects. Concentrations above 0,5 mg/l can cause acute [[toxic|toxicity]] for fishes. It has also been show to be able to act as an [[endocrine disrupting compounds|endocrine disruptor]] in vertebrates. As such it causes adverse effects on the development and reproduction of rats<ref name = OECD>[http://www.ospar.org/documents%5Cdbase%5Cpublications%5CP00270_BD%20on%20phthalates%20_2006%20version_.pdf OSPAR Commission, 2006: OSPAR background document on phthalates]</ref>.<P>  
  
Concentrations in sea water have been as high as 3 µg/l, although they are usually below 0,5 µg/l. Concentrations in sediments are below 2,4 mg/kg [[dry weight]] and usually around 0,01 mg/kg dry weight. <P>
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In sea water concentrations of 3 µg/l have been measured, although they are usually below 0,5 µg/l. Concentrations in sediments can reach 2,4 mg/kg [[dry weight]] but are usually around 0,01 mg/kg dry weight.<P>
  
Therefore there is a potential risk for ecotoxicological effects on aquatic species in the marine environment, but only at a local scale and mainly for organisms living in sediments. <ref name = OECD>[http://www.ospar.org/documents%5Cdbase%5Cpublications%5CP00270_BD%20on%20phthalates%20_2006%20version_.pdf OSPAR Commission, 2006: OSPAR background document on phthalates]</ref>
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There is a potential risk for ecotoxicological effects of dibutylphthalate on aquatic species in the marine environment, but only at a local scale and mainly for organisms living in sediments<ref name = OECD>[http://www.ospar.org/documents%5Cdbase%5Cpublications%5CP00270_BD%20on%20phthalates%20_2006%20version_.pdf OSPAR Commission, 2006: OSPAR background document on phthalates]</ref>.
 
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==References==
 
==References==
 
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{{author
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|AuthorID=19826
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|AuthorFullName=Daphnis De Pooter
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|AuthorName=Daphnisd}}
  
[[Category:Coastal and marine pollution]]
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[[Category:Toxicity chemicals]]

Latest revision as of 13:07, 9 August 2020

Definition of dibutylphthalate (DBP):
Dibutylphthalate belongs to the family of phthalates: industrial chemicals used as plasticizers, softeners, adhesives or solvents used by a variety of industries. They are used in PVC, paints, printing inks, cosmetics, coatings of cars,...[1].
This is the common definition for dibutylphthalate (DBP), other definitions can be discussed in the article

Notes

Dibutylphthalate
Dibutylphthalate
Formula
C16H2204
In 1998, 26.000 tons of dibutylphthalate ware produced in the EU of which 18.000 ton was consumed in the EU.

DBP can enter the marine environment through waste water effluents. Cleaning of road tankers releases DBP to the aquatic environment. DBP has a low water solubility (10 mg/l), and tends to adsorb to sediments. It is very stable but can be biodegraded, causing it to have an environmental half-life of 50 days. It has some potential to bioaccumulate in some organisms, however because of its biodegradability it is not expected to biomagnify through food chains.

Concentrations above 0,04 mg/l are shown to cause adverse effects on aquatic invertebrates and concentrations above 0,2 mg/l can have lethal effects. Concentrations above 0,5 mg/l can cause acute toxicity for fishes. It has also been show to be able to act as an endocrine disruptor in vertebrates. As such it causes adverse effects on the development and reproduction of rats[1].

In sea water concentrations of 3 µg/l have been measured, although they are usually below 0,5 µg/l. Concentrations in sediments can reach 2,4 mg/kg dry weight but are usually around 0,01 mg/kg dry weight.

There is a potential risk for ecotoxicological effects of dibutylphthalate on aquatic species in the marine environment, but only at a local scale and mainly for organisms living in sediments[1].


Environmental standards and legislation

Included in the OSPAR list of substances of priority action


See also

OSPAR background document on phthalates


References

The main author of this article is Daphnis De Pooter
Please note that others may also have edited the contents of this article.

Citation: Daphnis De Pooter (2020): Dibutylphthalate. Available from http://www.coastalwiki.org/wiki/Dibutylphthalate [accessed on 27-11-2024]