Difference between revisions of "Octylphenol"
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== Notes == | == Notes == | ||
| − | Octylphenol is in the EU produced (in 2001) at 23.000 tonnes per year. The main areas of use are as an intermediate in the production of phenol/formaldehyde resins and in the manufacture of octylphenol ethoxylates. These chemicals are used to in rubber, in pesticides and paints. Octylphenol mainly reaches the marine environment from waste waters from factories where it is used as an intermediate. Another possibility is from the breakdown of [[APE|alkylphenol ethoxylates]]. It has also been reported that octylphenol is present as an impurity in [[nonylphenol]] and that this may account to some extent for its detection in the environment. | + | Octylphenol is in the EU produced (in 2001) at 23.000 tonnes per year. The main areas of use are as an intermediate in the production of phenol/formaldehyde resins and in the manufacture of octylphenol ethoxylates. These chemicals are used to in rubber, in pesticides and paints. Octylphenol mainly reaches the marine environment from waste waters from factories where it is used as an intermediate. Another possibility is from the breakdown of [[APE|alkylphenol ethoxylates]]. It has also been reported that octylphenol is present as an impurity in [[nonylphenol]] and that this may account to some extent for its detection in the environment. <ref name = OECD>[http://www.ospar.org/documents%5Cdbase%5Cpublications%5Cp00273_BD%20on%20octylphenol%20_2006%20version.pdf OSPAR Commission, 2006: OSPAR background document on octylphenol]</ref> |
Considering the low vapour pressure of octylphenol and its tendency to adsorb to soils and sediments it can be expected that atmospheric concentrations will be low. Any octylphenol released to the atmosphere is likely to be degraded rapidly by reaction with hydroxyl radicals. In water and the soil however octylphenol is thought to be quite stable. It has a low tendency to [[bioaccumulation|bioaccumulate]] and no tendency to [[biomagnification|biomagnify]]. | Considering the low vapour pressure of octylphenol and its tendency to adsorb to soils and sediments it can be expected that atmospheric concentrations will be low. Any octylphenol released to the atmosphere is likely to be degraded rapidly by reaction with hydroxyl radicals. In water and the soil however octylphenol is thought to be quite stable. It has a low tendency to [[bioaccumulation|bioaccumulate]] and no tendency to [[biomagnification|biomagnify]]. | ||
It is a toxic substance, concentrations above 6,1 µg/l can already have adverse effects on marine organisms. | It is a toxic substance, concentrations above 6,1 µg/l can already have adverse effects on marine organisms. | ||
| − | The highest measured concentration (13 µg/l) has been measured in the English Tees [[estuary]]. Sediment concentrations in the Tees estuary could reach levels up to 0,32 mg/kg [[dry weight]]. Concentrations in coastal water are usually below 0,016 µg/l. Concentration is Noth Sea fish are bellow the limit of detection which is 0,004 mg/kg dry weight. In mammals and fishes it has been shown to be able to cause endocrine disruptive effects. | + | The highest measured concentration (13 µg/l) has been measured in the English Tees [[estuary]]. Sediment concentrations in the Tees estuary could reach levels up to 0,32 mg/kg [[dry weight]]. Concentrations in coastal water are usually below 0,016 µg/l. Concentration is Noth Sea fish are bellow the limit of detection which is 0,004 mg/kg dry weight. In mammals and fishes it has been shown to be able to cause [[endocrine disruptive compounds|endocrine disruptive effects]]. This because it displays estrogen like behavior.<ref name = OECD>[http://www.ospar.org/documents%5Cdbase%5Cpublications%5Cp00273_BD%20on%20octylphenol%20_2006%20version.pdf OSPAR Commission, 2006: OSPAR background document on octylphenol]</ref> |
| + | <P> | ||
| + | <BR> | ||
| + | <P> | ||
| + | == Environmental standards and legislation == | ||
| + | [[OSPAR List of priority substances|Included in the OSPAR list of substances of priority action]] | ||
| + | [[List of priority substances|Included in the water framework list of priority substances]] | ||
| + | <P> | ||
| + | <BR> | ||
| + | <P> | ||
| − | Octylphenol | + | == See also == |
| − | + | [http://www.vliz.be/projects/endis/EDnorth.php?showchemprop=true&showeffects=true&chemeffects=true&chemid=425 Octylphenol on the ED North Database] | |
| − | + | ||
| − | + | [http://www.ospar.org/documents%5Cdbase%5Cpublications%5Cp00273_BD%20on%20octylphenol%20_2006%20version.pdf OSPAR background document on octylphenol] | |
| + | <P> | ||
| + | <BR> | ||
| + | <P> | ||
| + | |||
| + | ==References== | ||
| + | <references/> | ||
| − | [ | + | [[Category:Coastal and marine pollution]] |
Revision as of 11:55, 7 August 2009
Definition of octylphenol:
The term octylphenol represents a large number of isomeric compounds. The octyl group may be branched in a variety of ways or be a straight chain and may be located at either the 2-, 3- or 4-position of the benzene ring. Of these potential isomers, 4-tertoctylphenol is the most commercially important. [1]
This is the common definition for octylphenol, other definitions can be discussed in the article
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Notes
Octylphenol is in the EU produced (in 2001) at 23.000 tonnes per year. The main areas of use are as an intermediate in the production of phenol/formaldehyde resins and in the manufacture of octylphenol ethoxylates. These chemicals are used to in rubber, in pesticides and paints. Octylphenol mainly reaches the marine environment from waste waters from factories where it is used as an intermediate. Another possibility is from the breakdown of alkylphenol ethoxylates. It has also been reported that octylphenol is present as an impurity in nonylphenol and that this may account to some extent for its detection in the environment. [1]
Considering the low vapour pressure of octylphenol and its tendency to adsorb to soils and sediments it can be expected that atmospheric concentrations will be low. Any octylphenol released to the atmosphere is likely to be degraded rapidly by reaction with hydroxyl radicals. In water and the soil however octylphenol is thought to be quite stable. It has a low tendency to bioaccumulate and no tendency to biomagnify. It is a toxic substance, concentrations above 6,1 µg/l can already have adverse effects on marine organisms.
The highest measured concentration (13 µg/l) has been measured in the English Tees estuary. Sediment concentrations in the Tees estuary could reach levels up to 0,32 mg/kg dry weight. Concentrations in coastal water are usually below 0,016 µg/l. Concentration is Noth Sea fish are bellow the limit of detection which is 0,004 mg/kg dry weight. In mammals and fishes it has been shown to be able to cause endocrine disruptive effects. This because it displays estrogen like behavior.[1]
Environmental standards and legislation
Included in the OSPAR list of substances of priority action
Included in the water framework list of priority substances
See also
Octylphenol on the ED North Database
OSPAR background document on octylphenol
