User:OliviaHall10/sandbox: Difference between revisions
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[[User:OliviaHall10|OliviaHall10]] ([[User talk:OliviaHall10|talk]]) 21:09, 19 February 2014 (UTC) |
[[User:OliviaHall10|OliviaHall10]] ([[User talk:OliviaHall10|talk]]) 21:09, 19 February 2014 (UTC) |
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{{chembox |
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| Verifiedfields = changed |
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| verifiedrevid = 402508915 |
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| ImageFile = Nonylphenolnew.png |
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| ImageSize = 160 px |
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| IUPACName = 4-(2,4-dimethylheptan-3-yl)phenol |
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| OtherNames = Phenol, nonyl- |
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| Section1 = {{Chembox Identifiers |
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| ChemSpiderID_Ref = {{chemspidercite|correct|chemspider}} |
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| ChemSpiderID = 60628 |
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| InChI = 1/C15H24O/c1-2-3-4-5-6-7-8-11-14-12-9-10-13-15(14)16/h9-10,12-13,16H,2-8,11H2,1H3 |
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| InChIKey = SNQQPOLDUKLAAF-UHFFFAOYAP |
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| StdInChI_Ref = {{stdinchicite|correct|chemspider}} |
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| StdInChI = 1S/C15H24O/c1-2-3-4-5-6-7-8-11-14-12-9-10-13-15(14)16/h9-10,12-13,16H,2-8,11H2,1H3 |
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| StdInChIKey_Ref = {{stdinchicite|correct|chemspider}} |
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| StdInChIKey = SNQQPOLDUKLAAF-UHFFFAOYSA-N |
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| CASNo_Ref = {{cascite|correct|CAS}} |
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| CASNo = 25154-52-3 |
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| CASNo1 = 104-40-5 |
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| CASNo2 = 84852-15-3 |
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| CASNo3 = 11066-49-2 |
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| PubChem = 67296 |
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| ChEMBL_Ref = {{ebicite|changed|EBI}} |
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| ChEMBL = 153062 |
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| SMILES = Oc1ccccc1CCCCCCCCC |
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}} |
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| Section2 = {{Chembox Properties |
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| Formula = C<sub>15</sub>H<sub>24</sub>O |
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| MolarMass = 220.35 g/mol |
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| Appearance = Light yellow viscous liquid with phenolic smell <ref name="GESTIS">{{GESTIS|ZVG=20610|Name=Nonylphenol, mixed isomers|Date=6 April 2011}}</ref> |
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| Density = 0.953 |
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| MeltingPt = −8 – 2 °C |
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| BoilingPt = 293 to 297 °C |
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| Solubility = 6 mg/L (pH 7) |
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}} |
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| Section3 = {{Chembox Hazards |
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| MainHazards = low level endrocrine disruptor |
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| FlashPt = |
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| Autoignition = |
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}} |
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}} |
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'''Nonylphenol''' is a family of closely related [[organic compound]]s, a subset of the [[alkylphenol]]s. This collection of compounds is a precursor to commercially important detergents. Nonylphenol features both polar and hydrophobic subunits, the [[phenol]] and the hydrocarbon tail. |
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==Production and basic properties== |
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The material known collectively as nonylphenol is produced by acid-catalyzed [[alkylation]] of [[phenol]] with a mixture of [[nonene]]s. Millions of kilograms are produced annually.<ref>Helmut Fiege, Heinz-Werner Voges, Toshikazu Hamamoto, Sumio Umemura, Tadao Iwata, Hisaya Miki, Yasuhiro Fujita, Hans-Josef Buysch, Dorothea Garbe, Wilfried Paulus "Phenol Derivatives" in Ullmann's Encyclopedia of Industrial Chemistry 2002, Wiley-VCH, Weinheim.{{DOI|10.1002/14356007.a19_313}}.</ref> The nonyl group, which is highly branched, attaches to the phenol ring via the 4- and, to lesser extent, the 2-positions. This mixture of isomers is usually available as a pale yellow liquid, although the pure compounds are colorless. The organic compound [[1-Nonyl-4-phenol|1-nonyl-4-phenol]] is not normally a component of what is marketed as nonylphenol. The nonylphenols are poorly soluble in water but soluble in alcohol. |
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In the environment, nonylphenols arise from the degradation of the nonaphenol ethoxylates, which are detergents. |
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=== Natural occurrences === |
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Nonylphenol has been found to be a component of the slime produced by the [[Velvet worm#Slime|velvet worm]] as a defence mechanism. |
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== Applications == |
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Alkylphenols are subjected to [[ethoxylation]] to give alkylphenol ethoxylates (APEs), which are widely used as industrial [[surfactant]]s. They are used in applications as disparate as the processing of wool and metals, as [[emulsifier]]s for [[emulsion polymerization]], as laboratory [[detergent]]s, and as [[pesticide]]s. APEs are a component of some household detergents outside of Europe. In Europe, due to environmental concerns, they have been replaced by more expensive [[Ethoxylation#Alcohol_ethoxylates_.28AE.27s.29|alcohol ethoxylates]], which are less problematic environmentally. [[Nonoxynol-9]], one of the APEs, is used as a surfactant in cleaning and cosmetic products, and as a [[spermicide]] in [[contraceptive]]s. |
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==Health and environmental hazards== |
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Nonylphenol is considered to be an [[endocrine disruptor]] due to weak ability to mimic estrogen and in turn disrupt the natural balance of hormones in affected organisms.<ref>"Review article: Nonylphenol in the environment: A critical review on occurrence, fate, toxicity and treatment in wastewaters" A. Soares, B. Guieysse, B. Jefferson, E. Cartmell, J.N. Lester Environment International 2008, Volume 34, Pages 1033-1049. {{DOI|10.1016/j.envint.2008.01.004}} PMID 18282600</ref><ref>Minnesota Pollution Control Agency Statewide Endocrine Disrupting Compound Monitoring Study, 2007 - 2008</ref><ref>[http://www.ewg.org/sites/humantoxome/chemicals/chemical.php?chemid=100371 Nonylphenol], [[Environmental Working Group]]</ref> The effect is weak because nonylphenols are not very close structural mimics of estradiol, but the levels of nonylphenol can be sufficiently high to compensate. |
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[[Image:NonylphenolEstradiol.png|thumb|350px|left|Structure of the hormone estradiol and one of the nonylphenols.]] |
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===Occurrence in the environment=== |
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Nonylphenols have been detected widely in waste water streams across the globe, which is a concern since it is toxic to many aquatic organisms. In the US, nonylphenols have been detected both in the Great Lakes and in the region of New York City.<ref>{{cite journal | journal = Science of the Total Environment | volume = 193 | issue = 3 | year = 1997 | pages = 263–275 | title = Occurrence of alkylphenols and alkylphenol mono- and diethoxylates in natural waters of the Laurentian Great Lakes and the upper St. Lawrence River | author = D. T. Bennie, C. A. Sullivan, H.-B. Lee, T. E. Peart and R. J. Maguire | doi = 10.1016/S0048-9697(96)05386-7}}</ref> In 1984, the formation of 4-nonylphenols from [[nonylphenol ethoxylates]] in [[Sewage treatment|wastewater treatment plants]] was first discovered.<ref>{{cite journal | author = [[Walter Giger|W. Giger]], P. H. Brunner, C. Schaffner | title = 4-Nonylphenol in sewage sludge: accumulation of toxic metabolites from nonionic surfactants | journal = Science | volume = 225 | issue = 4662 |year = 1984 | pages = 623–625 | doi = 10.1126/science.6740328 | pmid = 6740328}}</ref> Nonylphenol is persistent in the environment,<ref>Dayue Y. Shang, Robie W. Macdonald, and Michael G. Ikonomou. 1999. Persistence of Nonylphenol Ethoxylate Surfactants and Their Primary Degradation Products in Sediments from near a Municipal Outfall in the Strait of Georgia, British Columbia, Canada, Environmental Science and Technology 33 (9), pp 1366–1372</ref> therefore lingers with the potential to negatively affect organisms it comes in contact with. |
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=== Environmental protection policies === |
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Nonylphenol and nonyphenol ethoxylates have been restricted in the European Union as a hazard to human and environmental safety.<ref>Official Journal of the European Union: [http://eur-lex.europa.eu/LexUriServ/LexUriServ.do?uri=OJ:L:2003:178:0024:0027:EN:PDF DIRECTIVE 2003/53/EC OF THE EUROPEAN PARLIAMENT AND OF THE COUNCIL of 18 June 2003 amending for the 26th time Council Directive 76/769/EEC relating to restrictions on the marketing and use of certain dangerous substances and preparations (nonylphenol, nonylphenol ethoxylate and cement)], July 17, 2003</ref> |
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For freshwater ecosystems, the Environmental Protection Agency has set two types of standards, acute and chronic. The acute criteria is a one-hour average concentration of nonylphenol not to exceed 28 μg/L more than once every three years on the average in order to protect fresh water aquatic life and their uses. The chronic criteria is a four-hour average concentration of nonylphenol not to exceed 6.6 μg/L more than once every three years on average.<ref name=EPA>[http://www.epa.gov/waterscience/criteria/nonylphenol/nonylphenol-fs.html Aquatic Life Criteria for Nonylphenol], [[United States Environmental Protection Agency]]</ref> |
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For saltwater ecosystems, the acute criteria is set at 7.0 μg/L and the chronic criteria is set at 1.7 μg/L. <ref name=EPA/> |
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== References == |
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{{Reflist}} |
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[[Category:Phenolic lipids]] |
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[[Category:Endocrine disruptors]] |
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[[User:OliviaHall10|OliviaHall10]] ([[User talk:OliviaHall10|talk]]) 16:47, 13 March 2014 (UTC) |
Revision as of 16:47, 13 March 2014
Chemical structure and properties
Nonylphenols fall into the general chemical category of alkylphenols. Another alkylphenol is Bisphenol-A, which is found in plastic water bottles. [1] The structure of NPs may vary. The nonyl group can be attached to the phenol ring at various locations, usually the 4- and, to lesser extent, the 2-positions, and can be either branched or linear. A branched nonylphenol, 4-nonylphenol, is the most widely produced and marketed nonylphenol. [2] The mixture of nonylphenol isomers is a pale yellow liquid, although the pure compounds are colorless. The nonylphenols are moderatley soluble in water [3] but soluble in alcohol.
Nonylphenol arises from the degradation of Nonylphenol ethoxylates in the environment. Nonylphenol ethoxylates fall into the general chemical category of alkylphenol ethoxylates APEs. NPEs are a clear to light orange color liquid. Nonylphenol ethoxylates are nonionic in water, which means that they have no charge. Because of this property they are used as detergents, cleaners, emulsfiers, and a variety of other applications. They are hydrophilic, water loving, at one end and hydrophobic, water fearing, at the other end, which allows them to surround non-polar substances like oil and grease, and exclude them from water.
Production
Nonylphenols are produced by acid-catalyzed alkylation of phenol with a mixture of nonenes. To make NPEs manufacturer's react NP with ethlylene oxide under basic conditions. [4] Approximately 100 to 500 millions pounds of nonylphenol are produced anualy, based on the most widely produced nonylphenols.[5]
Uses
Nonylphenol is used in manufacturing antiooxidants, lubricating oil additives and the production of NPEs. Nonylphenol exthoxylates have a variety of industrial and household uses including detergents, emulsifiers, wetting and dispersing agents, antistatic agents, demulsifiers and solubilisers. [6]
Another surfactant nonoxynol, which was once used as intravaginal spermicide and condom lubricant was found to metabolize into free nonylphenol when administered to lab animals. [7]
Occurrence in the environment
- Water supplies—we will discuss how manufacturers release NPs and NPEs into the environment and how they subsequently enter water systems.
In aquatic environments waste from sewage treatment plants are the main source nonylphenol. Nonylphenol is found in river water and sediments as well as soil and groundwater. In surface water the concentration of nonylphenol will decrease due to photolysis induced by sunlight, but in sediment it is estimated that is has a half life of mare than 60 years. [8] Due to its low solubility it is found in higher concentrations in sediment versus in water.
The occurrence of nonylphenol in soil is not as well studied as in aquatic environment, but the major concern is in sewage sludge that is recycled into agricultural land. There are many factors that influence the degradation of nonylphenol in soil including the depth of the sludge layer oxygen availability and contaminant bioavailability. Mobility of nonylphenol in soil is low.
Environmental Hazards
- Aquatic toxicity
The effects of nonylphenol in the environment are the feminization of aquatic organisms, decreased male fertility, and decreased survival in young fish. [9] Nonylphenol can cause endocrine disruption in fish by interacting with estrogen receptors and androgen receptors. In the liver NP can disrupt steriodgenesis and can interfere with the level of FSH (follicle-stimulating hormone) released from the pituitary Concentrations of NP that inhibit reproductive development and function in fish also damaged kidneys, decreased body weight, and induced a stressed behavior. [10]
Human Exposure
Diet seems the most significant source of exposure of NPs to humans. For example, food samples were found with concentrations ranging from 0.1 to 19.4 µg/kg in a diet survey in Germany. In Taiwan NP concentrations in food ranged from 5.8 to 235.8 µg/kg. Seafood in particular was found to have a high concentration of NP. [11]
Drinking water does not represent a significant source of exposure in comparison to other sources such as food packing materials, cleaning products, and carious skin care products. Concentrations of nonylphenol in treated drinking water varied from 85 ng/l in Spain to 15 ng/l in Germany. [12]
Health Hazards
- Toxicity—provide levels of exposure that have been to cause adverse effects.
- Endocrine Disruption—discuss what physiological effects are seen in model organisms (mice). For example: decreases in epididymal sperm density or testicular sperm head counts, increased in estrous cycle length, etc.
Alkylphenols like nonylphenol and Bisphenol-A were found to have estrogenic effects in the body. They are also known as xenoestrogens. [13] Estrogenic substances and other endocrine disruptors are compounds that have hormone-like effects in both wildlife and humans. Xenoestrogens usually function by binding to estrogen receptors and acting competitively toward natural estrogens. Alkylphenols like nonylphenol and related compounds are found in pesticides and industrial chemicals. Nonylphenol was discovered to have hormone like affects accidentally because it contaminated other experiments in laboratories that were studying natural estrogens that were using polystyrene tubes. The detergent nonylphenol is harmful when it degrades into nonylphenol ethoxylate in sewage treatment plants. [14] Unfortunately there limited articles on the endocrine activity of nonylphenol in comparison to BPA. One study conducted in Italian women showed that nonylphenol was one of the highest contaminants at a concentration of 32 ng/mL in breast milk when compared to other alkylphenols octylphenol, nonylphenol monoethoxylate, and two octylphenol ethoxylates. The study found a positive correlation between fish consumption and the concentration of NP in breast milk. [15] This is a large problem because breast milk is the main source of nourishment for newborns, who are in early stages of development where hormones are very influential. Elevated levels of endocrine disruptors in breast milk have been associated with negative affects on neurological development, growth and memory function.
Nonylphenol is also capable of inducing breast tumore cell proliferation. [16]
Protection policies
The European Union has included NP on the list of priority hazardous substances for surface water in the Water Framework Directive. They are now implementing a drastic reduction policy of NP's in surface waterways. The Environmental quality standard for NP was proposed to be 0.3 ug/l. In the USA, the EPA set criteria that recommended the NP concentration shoudl not exceed 6.6 ug/l in fresh water and 1.7 ug/l in saltwater. In other Asian and South American countries there is still a large about of APE's and little regulation. [17]
OliviaHall10 (talk) 21:09, 19 February 2014 (UTC)
current page:
Names | |
---|---|
IUPAC name
4-(2,4-dimethylheptan-3-yl)phenol
| |
Other names
Phenol, nonyl-
| |
Identifiers | |
3D model (JSmol)
|
|
ChEMBL | |
ChemSpider | |
PubChem CID
|
|
| |
| |
Properties | |
C15H24O | |
Molar mass | 220.35 g/mol |
Appearance | Light yellow viscous liquid with phenolic smell [18] |
Density | 0.953 |
Melting point | −8 – 2 °C |
Boiling point | 293 to 297 °C |
6 mg/L (pH 7) | |
Hazards | |
Occupational safety and health (OHS/OSH): | |
Main hazards
|
low level endrocrine disruptor |
Except where otherwise noted, data are given for materials in their standard state (at 25 °C [77 °F], 100 kPa).
|
Nonylphenol is a family of closely related organic compounds, a subset of the alkylphenols. This collection of compounds is a precursor to commercially important detergents. Nonylphenol features both polar and hydrophobic subunits, the phenol and the hydrocarbon tail.
Production and basic properties
The material known collectively as nonylphenol is produced by acid-catalyzed alkylation of phenol with a mixture of nonenes. Millions of kilograms are produced annually.[19] The nonyl group, which is highly branched, attaches to the phenol ring via the 4- and, to lesser extent, the 2-positions. This mixture of isomers is usually available as a pale yellow liquid, although the pure compounds are colorless. The organic compound 1-nonyl-4-phenol is not normally a component of what is marketed as nonylphenol. The nonylphenols are poorly soluble in water but soluble in alcohol.
In the environment, nonylphenols arise from the degradation of the nonaphenol ethoxylates, which are detergents.
Natural occurrences
Nonylphenol has been found to be a component of the slime produced by the velvet worm as a defence mechanism.
Applications
Alkylphenols are subjected to ethoxylation to give alkylphenol ethoxylates (APEs), which are widely used as industrial surfactants. They are used in applications as disparate as the processing of wool and metals, as emulsifiers for emulsion polymerization, as laboratory detergents, and as pesticides. APEs are a component of some household detergents outside of Europe. In Europe, due to environmental concerns, they have been replaced by more expensive alcohol ethoxylates, which are less problematic environmentally. Nonoxynol-9, one of the APEs, is used as a surfactant in cleaning and cosmetic products, and as a spermicide in contraceptives.
Health and environmental hazards
Nonylphenol is considered to be an endocrine disruptor due to weak ability to mimic estrogen and in turn disrupt the natural balance of hormones in affected organisms.[20][21][22] The effect is weak because nonylphenols are not very close structural mimics of estradiol, but the levels of nonylphenol can be sufficiently high to compensate.
Occurrence in the environment
Nonylphenols have been detected widely in waste water streams across the globe, which is a concern since it is toxic to many aquatic organisms. In the US, nonylphenols have been detected both in the Great Lakes and in the region of New York City.[23] In 1984, the formation of 4-nonylphenols from nonylphenol ethoxylates in wastewater treatment plants was first discovered.[24] Nonylphenol is persistent in the environment,[25] therefore lingers with the potential to negatively affect organisms it comes in contact with.
Environmental protection policies
Nonylphenol and nonyphenol ethoxylates have been restricted in the European Union as a hazard to human and environmental safety.[26]
For freshwater ecosystems, the Environmental Protection Agency has set two types of standards, acute and chronic. The acute criteria is a one-hour average concentration of nonylphenol not to exceed 28 μg/L more than once every three years on the average in order to protect fresh water aquatic life and their uses. The chronic criteria is a four-hour average concentration of nonylphenol not to exceed 6.6 μg/L more than once every three years on average.[27]
For saltwater ecosystems, the acute criteria is set at 7.0 μg/L and the chronic criteria is set at 1.7 μg/L. [27]
References
- ^ Sonnenschein, Carlos, and Ana M. Soto. "An Updated Review of Environmental Estrogen and Androgen Mimics and Antagonists." The Journal of Steroid Biochemistry and Molecular Biology 65.1-6 (1998): 143-50.
- ^ EPA. 2010. Nonylphenol (NP) and Nonylphenal Ethoxylates (NPEs) Action Plan. February, 2014.
- ^ EPA. 2010. Nonylphenol (NP) and Nonylphenal Ethoxylates (NPEs) Action Plan. February, 2014.
- ^ EPA. 2010. Nonylphenol (NP) and Nonylphenal Ethoxylates (NPEs) Action Plan. February, 2014.
- ^ EPA. 2010. Nonylphenol (NP) and Nonylphenal Ethoxylates (NPEs) Action Plan. February, 2014.
- ^ Soares, A., B. Guieysse, B. Jefferson, E. Cartmell, and J.n. Lester. "Nonylphenol in the Environment: A Critical Review on Occurrence, Fate, Toxicity and Treatment in Wastewaters." Environment International 34.7 (2008): 1033-049.
- ^ Sonnenschein, Carlos, and Ana M. Soto. "An Updated Review of Environmental Estrogen and Androgen Mimics and Antagonists." The Journal of Steroid Biochemistry and Molecular Biology 65.1-6 (1998): 143-50.
- ^ Soares, A., B. Guieysse, B. Jefferson, E. Cartmell, and J.n. Lester. "Nonylphenol in the Environment: A Critical Review on Occurrence, Fate, Toxicity and Treatment in Wastewaters." Environment International 34.7 (2008): 1033-049.
- ^ Soares, A., B. Guieysse, B. Jefferson, E. Cartmell, and J.n. Lester. "Nonylphenol in the Environment: A Critical Review on Occurrence, Fate, Toxicity and Treatment in Wastewaters." Environment International 34.7 (2008): 1033-049.
- ^ Katherine E. Liney, Josephine A. Hagger, Charles R. Tyler, Michael H. Depledge, Tamara S. Galloway, Susan Jobling. "Health Effects in Fish of Long-Term Exposure to Effluents from Wastewater Treatment Works." Environ Health Perspect. 2006 April; 114(Suppl 1): 81–89. Published online 2005 October 21. doi: 10.1289/ehp.8058
- ^ Ademollo et al., 2008 N. Ademollo, F. Ferrara, M. Delise, F. Fabietti, E. Funari Nonylphenol and octylphenol in human breast milk. Environ. Int., 34 (2008), pp. 984–987
- ^ Soares, A., B. Guieysse, B. Jefferson, E. Cartmell, and J.n. Lester. "Nonylphenol in the Environment: A Critical Review on Occurrence, Fate, Toxicity and Treatment in Wastewaters." Environment International 34.7 (2008): 1033-049.
- ^ Asimakopoulos, Alexandros G., Nikolaos S. Thomaidis, and Michael A. Koupparis. "Recent Trends in Biomonitoring of Bisphenol A, 4-t-octylphenol, and 4-nonylphenol." Toxicology Letters 210.2 (2012): 141-54. Web.
- ^ Sonnenschein, Carlos, and Ana M. Soto. "An Updated Review of Environmental Estrogen and Androgen Mimics and Antagonists." The Journal of Steroid Biochemistry and Molecular Biology 65.1-6 (1998): 143-50.
- ^ Ademollo et al., 2008 N. Ademollo, F. Ferrara, M. Delise, F. Fabietti, E. Funari Nonylphenol and octylphenol in human breast milk. Environ. Int., 34 (2008), pp. 984–987
- ^ Soares, A., B. Guieysse, B. Jefferson, E. Cartmell, and J.n. Lester. "Nonylphenol in the Environment: A Critical Review on Occurrence, Fate, Toxicity and Treatment in Wastewaters." Environment International 34.7 (2008): 1033-049.
- ^ A. David, H. Fenet, E. Gomez "Alkylphenols in marine environments: distribution monitoring strategies and detection considerations". Mar. Pollut. Bull., 58 (2009), pp. 953–960
- ^ Record of Nonylphenol, mixed isomers in the GESTIS Substance Database of the Institute for Occupational Safety and Health, accessed on 6 April 2011.
- ^ Helmut Fiege, Heinz-Werner Voges, Toshikazu Hamamoto, Sumio Umemura, Tadao Iwata, Hisaya Miki, Yasuhiro Fujita, Hans-Josef Buysch, Dorothea Garbe, Wilfried Paulus "Phenol Derivatives" in Ullmann's Encyclopedia of Industrial Chemistry 2002, Wiley-VCH, Weinheim.doi:10.1002/14356007.a19_313.
- ^ "Review article: Nonylphenol in the environment: A critical review on occurrence, fate, toxicity and treatment in wastewaters" A. Soares, B. Guieysse, B. Jefferson, E. Cartmell, J.N. Lester Environment International 2008, Volume 34, Pages 1033-1049. doi:10.1016/j.envint.2008.01.004 PMID 18282600
- ^ Minnesota Pollution Control Agency Statewide Endocrine Disrupting Compound Monitoring Study, 2007 - 2008
- ^ Nonylphenol, Environmental Working Group
- ^ D. T. Bennie, C. A. Sullivan, H.-B. Lee, T. E. Peart and R. J. Maguire (1997). "Occurrence of alkylphenols and alkylphenol mono- and diethoxylates in natural waters of the Laurentian Great Lakes and the upper St. Lawrence River". Science of the Total Environment. 193 (3): 263–275. doi:10.1016/S0048-9697(96)05386-7.
{{cite journal}}
: CS1 maint: multiple names: authors list (link) - ^ W. Giger, P. H. Brunner, C. Schaffner (1984). "4-Nonylphenol in sewage sludge: accumulation of toxic metabolites from nonionic surfactants". Science. 225 (4662): 623–625. doi:10.1126/science.6740328. PMID 6740328.
{{cite journal}}
: CS1 maint: multiple names: authors list (link) - ^ Dayue Y. Shang, Robie W. Macdonald, and Michael G. Ikonomou. 1999. Persistence of Nonylphenol Ethoxylate Surfactants and Their Primary Degradation Products in Sediments from near a Municipal Outfall in the Strait of Georgia, British Columbia, Canada, Environmental Science and Technology 33 (9), pp 1366–1372
- ^ Official Journal of the European Union: DIRECTIVE 2003/53/EC OF THE EUROPEAN PARLIAMENT AND OF THE COUNCIL of 18 June 2003 amending for the 26th time Council Directive 76/769/EEC relating to restrictions on the marketing and use of certain dangerous substances and preparations (nonylphenol, nonylphenol ethoxylate and cement), July 17, 2003
- ^ a b Aquatic Life Criteria for Nonylphenol, United States Environmental Protection Agency
OliviaHall10 (talk) 16:47, 13 March 2014 (UTC)