Phthalates 

General chemical structure of phthalates. R and R' = CnH2n+1; n = 4-15

Phthalates, or phthalate esters, are esters of phthalic acid and are mainly used as plasticizers (substances added to plastics to increase their flexibility). They are chiefly used to soften polyvinyl chloride. Phthalates are being phased out of many products in the United States and European Union over health concerns.

Contents

Uses

Phthalates are used in a large variety of products, from enteric coatings of pharmaceutical pills to viscosity control agents, gelling agents, film formers, stabilizers, dispersants, lubricants, binders, emulsifying agents, and suspending agents. End applications include adhesives and glues, agricultural adjuvants, building materials, personal care products, detergents and surfactants, plastic objects, paints, printing inks and coatings, pharmaceuticals, food products and textiles.

Phthalates are also frequently used in soft plastic fishing lures, nail polish, adhesives, caulk, paint pigments, and toys made of so-called "jelly rubber." Phthalates are used in a variety of household applications (shower curtains, adhesives, perfume), modern pop-culture electronics and medical applications such as catheters. The most widely-used phthalates are the di-2-ethyl hexyl phthalate (DEHP), the diisodecyl phthalate (DIDP) and the diisononyl phthalate (DINP). DEHP is the dominant plasticizer used in PVC, due to its low cost. Benzylbutylphthalate (BBzP) is used in the manufacture of foamed PVC, which is mostly used as a flooring material. Phthalates with small R and R' groups are used as solvents in perfumes and pesticides.

As of 2004, manufacturers produced about 363 thousand metric tonnes (800 million pounds or 400 000 short tons) of phthalates each year.

History

Phthalates were first produced during the 1920s, and have been produced in large quantities since the 1950s, when PVC was introduced.

Properties

Phthalate esters are the dialkyl or alkyl aryl esters of phthalic acid (also called 1,2-benzenedicarboxylic acid, not be confused with the isomeric terephthalic or isophthalic acids ); the name phthalate derives from phthalic acid, which itself is derived from word "naphthalene". When added to plastics, phthalates allow the long polyvinyl molecules to slide against one another. The phthalates show low water solubility, high oil solubility, and low volatility. The polar carboxyl group contributes little to the physical properties of the phthalates, except when R and R' are very small (such as ethyl or methyl groups).citation needed They are colorless, odorless liquids produced by reacting phthalic anhydride with an appropriate alcohol (usually 6 to 13 carbon).

Table of the most common phthalates

Name Acronym Structural formula CAS No.
Dimethyl phthalate DMP C6H4(COOCH3)2 131-11-3
Diethyl phthalate DEP C6H4(COOC2H5)2 84-66-2
Diallyl phthalate DAP C6H4(COOCH2CH=CH2)2 131-17-9
Di-n-propyl phthalate DPP C6H4[COO(CH2)2CH32 131-16-8
Di-n-butyl phthalate DBP C6H4[COO(CH2)3CH32 84-74-2
Diisobutyl phthalate DIBP C6H4[COOCH2CH(CH3)22 84-69-5
Butyl cyclohexyl phthalate BCP CH3(CH2)3OOCC6H4COOC6H11 84-64-0
Di-n-pentyl phthalate DNPP C6H4[COO(CH2)4CH32 131-18-0
Dicyclohexyl phthalate DCP C6H4[COOC6H112 84-61-7
Butyl benzyl phthalate BBP CH3(CH2)3OOCC6H4COOCH2C6H5 85-68-7
Di-n-hexyl phthalate DNHP C6H4[COO(CH2)5CH32 84-75-3
Diisohexyl phthalate DIHxP C6H4[COO(CH2)3CH(CH3)22 146-50-9
Diisoheptyl phthalate DIHpP C6H4[COO(CH2)4CH(CH3)22 41451-28-9
Butyl decyl phthalate BDP CH3(CH2)3OOCC6H4COO(CH2)9CH3 89-19-0
Di(2-ethylhexyl) phthalate DEHP, DOP C6H4[COOCH2CH(C2H5)(CH2)3CH32 117-81-7
Di(n-octyl) phthalate DNOP C6H4[COO(CH2)7CH32 117-84-0
Diisooctyl phthalate DIOP C6H4[COO(CH2)5CH(CH3)22 27554-26-3
n-Octyl n-decyl phthalate ODP CH3(CH2)7OOCC6H4COO(CH2)9CH3 119-07-3
Diisononyl phthalate DINP C6H4[COO(CH2)6CH(CH3)22 28553-12-0
Diisodecyl phthalate DIDP C6H4[COO(CH2)7CH(CH3)22 26761-40-0
Diundecyl phthalate DUP C6H4[COO(CH2)10CH32 3648-20-2
Diisoundecyl phthalate DIUP C6H4[COO(CH2)8CH(CH3)22 85507-79-5
Ditridecyl phthalate DTDP C6H4[COO(CH2)12CH32 119-06-2
Diisotridecyl phthalate DIUP C6H4[COO(CH2)10CH(CH3)22 68515-47-9

Health effects

Exposure

People are commonly exposed to phthalates, and the majority of Americans tested by the Centers for Disease Control and Prevention have metabolites of multiple phthalates in their urine. Diet is believed to be the main source of DEHP and other phthalates in the general population, although inhalational exposure is also significant.1 Baby care products containing phthalates are a source of exposure for infants. The authors of a 2008 study "observed that reported use of infant lotion, infant powder, and infant shampoo were associated with increased infant urine concentrations of [phthalate metabolites], and this association is strongest in younger infants. These findings suggest that dermal exposures may contribute significantly to phthalate body burden in this population." Though they did not examine health outcomes, they noted that "Young infants are more vulnerable to the potential adverse effects of phthalates given their increased dosage per unit body surface area, metabolic capabilities, and developing endocrine and reproductive systems."2

Some vendors of jelly rubber sex toys advise covering them in condoms when used internally, due to the possible leaching of phthalates. Other vendors do not carry jelly rubber sex toys, in favor of phthalate-free varieties.3

Endocrine disruption

In studies of rodents exposed to certain phthalates, high doses have been shown to change hormone levels and cause birth defects.1 A recent British study showed that the phthalate di(n-butyl) phthalate (DBP) or its metabolite monobutyl phthalate (MBP) suppresses steroidogenesis by fetal-type Leydig cells in primates as in rodents.4

A seminal5 study by Swan et al. published in 2005 reported that human phthalate exposure during pregnancy resulted in decreased anogenital distance among baby boys later born, a change that in rodents exposed to phthalates is associated with genital abnormalities. In this study phthalate metabolites were measured in urine samples collected from pregnant women. Upon birth, the genital features and anogenital distance of these women's babies were measured and correlated with the residue levels in the mother's urine. Boys born to mothers with the highest levels of phthalates were 7 times more likely to have a shortened anogenital distance.6 While anogenital distance is routinely used as a measure of fetal exposure to endocrine disruptors in animals,7 the parameter has only recently been assessed in humans.8 Another of these studies states that "Whether anogenital distance measurements in humans relate to clinically important outcomes … remains to be determined,"9 and a National Toxicology Program expert panel concluded that anogenital distance is a "'novel index' whose relevance in humans 'has not been established,'" and that there is "insufficient evidence in humans" that DEHP causes harm.10 Still, the Swan study has been widely cited, and "suggest[s] that male reproductive development in humans could be affected by prenatal exposure to environmentally relevant levels of phthalates."5 Authors of a more recent study of boys with undescended testis suggested that exposure to a combination of phthalates and anti-androgenic pesticides may have contributed to that condition.11

In contrast to the Swan study, an earlier study found that "adolescents exposed to significant quantities of DEHP as neonates showed no significant adverse effects on their physical growth and pubertal maturity."12 This study, however, examined children exposed intravenously to phthalate diesters, and intravenous exposure results in relatively little metabolic conversion of the relatively nontoxic phthalate diester to its toxic monoester metabolite.13

Other effects

Large amounts of specific phthalates fed to rodents have been show to damage to their liver and testes,1 and initial rodent studies also indicated hepatocarcinogenity. Following this result, diethyl hexyl phthalate was listed as a possible carcinogen by IARC, EC and WHO. Later studies on primates showed that the mechanism was specific to rodents - humans are resistant to the effect.14 The carcinogen classification was subsequently withdrawn.

In 2004, a joint Swedish-Danish research team found a very strong link between allergies in children and the phthalates DEHP and BBzP.15 The first systematic review of the evidence relating phthalates to asthma found evidence of association between phthalates in the home and asthma especially in children, but this evidence was limited by imprecise data on exact levels of exposure. Phthalates migrate from PVC plastics and into the dust, where they may be inhaled.16

In 2007, a cross-sectional study of U.S. males concluded that urine concentrations of four phthalate metabolites correlate with waist size and three phthalate metabolites correlate with the cellular resistance to insulin, a precursor to Type II diabetes. The authors note the need for follow-up longitudinal studies,17 as waist size is known to correlate with insulin resistance.

Legal status

European Union

The use of some phthalates has been restricted in the European Union for use in children's toys since 1999.18 DEHP, BBP, and DBP are restricted for all toys; DINP, DIDP, and DNOP are restricted only in toys that can be taken into the mouth. The restriction states that the amount of phthalates may not be greater than 0.1% mass percent of the plasticized part of the toy. These phthalates are allowed at any concentration in other products and other phthalates are not restricted.

There are no other specific restrictions in the European Union although draft proposals have been tabled for the inclusion of BBP, DEHP and DBP on the Candidate list of Substances for Authorisation under REACH.19 Fourteen other countries, including Japan, Argentina, and Mexico, have also banned phthalates from children's toys.20 The Dutch office of Greenpeace UK sought to encourage the European Union to ban sex toys that contained phthalates.21

United States

Some phthalates will be restricted in the U.S. state of California (for children's toys) starting in 2009.22 In Connecticut, state legislators are considering a bill that would ban phthalates in children's products.23 Following California, the U.S. Congress passed a bill restricting three types of phthalates permanently and put interim restrictions on three others, effective February 10, 200924. President Bush signed the bill into law on August 14, 2008.25

Identification in plastics

Some type 3 plastics may leach phthalates.citation needed

Phthalates are used in some but not all PVC formulations, and there are no labeling requirements for phthalates specifically. PVC plastics are typically used for various containers and hard packaging, medical tubing and bags, and are labelled "Type 3" for recycling reasons. However, the presence of phthalates rather than other plasticizers is not marked on PVC items, and thus it is not possible to identify phthalate-containing items by markings alone.

Chemical analysis, for example by gas chromatography, can establish the presence of phtalates.

See also

References

  1. ^ a b c Third National Report on Human Exposure to Environmental Chemicals, U.S. CDC, July 2005.
  2. ^ Sathyanarayana, Sheela. "Baby Care Products:Possible sources of infant phthalate exposure PMID 18245401" (full text article). Retrieved on 2008-02-12.
  3. ^ Sustainable Kink. A local couple explores the last eco-frontier: sex toys. by Ethan Smith, "Willamette Week" 18 April 2007.
  4. ^ Hallmark N, Walker M, McKinnell C, Mahood IK, Scott H, Bayne R, Coutts S, Anderson RA, Greig I, Morris K, Sharpe RM. (2007). "Effects of monobutyl and di(n-butyl) phthalate in vitro on steroidogenesis and Leydig cell aggregation in fetal testis explants from the rat: comparison with effects in vivo in the fetal rat and neonatal marmoset and in vitro in the human". Environ Health Perspect. 115 (3): 390–6.. doi:10.1289/ehp.9490. PMID 17431488, http://www.pubmedcentral.nih.gov/articlerender.fcgi?tool=pubmed&pubmedid=17431488. 
  5. ^ a b Tilson HA (June 2008). "EHP Papers of the Year, 2008". Environ. Health Perspect. 116 (6): A234. doi:10.1289/ehp.11684. PMID 18560492. 
  6. ^ Swan, S.H. et al. 2005. PMID 16079079 An overview of this paper is given in the same volume: Julia R. Barrett, Phthalates and Baby Boys: Potential Disruption of Human Genital Development, Environ Health Perspect. 2005 Aug; 113(8): A542. [1]
  7. ^ Salazar-Martinez E, Romano-Riquer P, Yanez-Marquez E, Longnecker MP, Hernandez-Avila M (2004). "Anogenital distance in human male and female newborns: a descriptive, cross-sectional study". Environ Health 3 (1): 8. doi:10.1186/1476-069X-3-8. PMID 15363098. PMC: 521084, http://www.ehjournal.net/content/3/1/8. Retrieved on 20 June 2008. 
  8. ^ Postellon, Daniel C. (2008). "Baby Care Products" (letter). Pediatrics 121 (6 (June)): 1292. doi:10.1542/peds.2008-0401. PMID 18519505, http://pediatrics.aappublications.org/cgi/content/full/121/6/1292. 
  9. ^ Romano-Riquer SP, Hernández-Avila M, Gladen BC, Cupul-Uicab LA, Longnecker MP (2007). "Reliability and determinants of anogenital distance and penis dimensions in male newborns from Chiapas, Mexico". Paediatr Perinat Epidemiol 21 (3): 219–28. doi:10.1111/j.1365-3016.2007.00810.x. PMID 17439530. 
  10. ^ Kaiser J. Toxicology. Panel finds no proof that phthalates harm infant reproductive systems Science 2005 Oct 21;310(5747):422 PMID 16239449
  11. ^ Toppari J, Virtanen H, Skakkebaek NE, Main KM (2006). "Environmental effects on hormonal regulation of testicular descent". J Steroid Biochem Mol Biol 102 (1-5): 184–6. doi:10.1016/j.jsbmb.2006.09.020. PMID 17049842. 
  12. ^ Khodayar Rais-Bahram (9 2004). "Follow-Up Study of Adolescents Exposed to Di(2-Ethylhexyl) Phthalate (DEHP) as Neonates on Extracorporeal Membrane Oxygenation (ECMO) Support" (pdf) 2. Environmental Health Perspectives. Retrieved on 2007 - 01 - 25.
  13. ^ Huber WW, Grasl-Kraupp B, Schulte-Hermann R. (1996). "Hepatocarcinogenic potential of di(2-ethylhexyl)phthalate in rodents and its implications on human risk". Crit Rev Toxicol 26 (4): 365–481. doi:10.3109/10408449609048302. PMID 8817083. 
  14. ^ http://www.cpsc.gov/library/foia/foia01/os/dinp.pdf p. 87.
  15. ^ C.-G. Bornehag, J. Sundell, C. J. Weschler, T. Sigsgaard, B. Lundgren, M. Hasselgren, L. Hägerhed-Engman (2004). "The Association between Asthma and Allergic Symptoms in Children and Phthalates in House Dust: A Nested Case–Control Study". Environ Health Perspect. 112 (13): 1319–1340. doi:10.1289/ehp.7187. 
  16. ^ The Role of Exposure to Phthalates from Polyvinyl Chloride Products in the Development of Asthma and Allergies: A Systematic Review and Meta-analysis
  17. ^ Stahlhut RW, van Wijngaarden E, Dye TD, Cook S, Swan SH. (2007). "Concentrations of urinary phthalate metabolites are associated with increased waist circumference and insulin resistance in adult u.s. Males". Environ Health Perspect 115 (6): 876–82. PMID 17589594. 
  18. ^ Ban of phthalates in childcare articles and toys, press release IP/99/829, 10 November 1999
  19. ^ ECHA Website - Proposal for identification of Substances of Very High Concern
  20. ^ Phthalates and Children's Products
  21. ^ News24
  22. ^ California Bans Phthalates In Toys For Children, Bette Hileman, Chemical and Engineering News, OCT. 22, 2007, P. 12.
  23. ^ Weil, William (April 23, 2008), "Debate In A Bottle" (dead linkScholar search), Hartford Courant, http://www.courant.com/features/lifestyle/green/hc-bottled.art0apr23,0,5170837.story .
  24. ^ Toys Containing Banned Plastics Still on Market (http://online.wsj.com/article/SB122472242723860917.html?mod=googlenews_wsj)
  25. ^ American chemistry council has mixed response to passage of consumer product safety modernization act, retrieved on 2008-11-11

Further reading

External links

Media

Research

Sources suggesting low/no health risks