-Caveat Lector-

             RACHEL'S ENVIRONMENT & HEALTH WEEKLY #603
                        ---June 18, 1998---

 EXPERIMENTING ON CHILDREN

 by Charlie Cray

 Health authorities in several European countries, including
 Austria, Belgium, Denmark, Germany, and the Netherlands have
 recommended a ban on soft PVC toys, such as teething rings and
 bath toys.  The Spanish government requested action by the
 European Union (EU) in March, 1998. PVC, or polyvinyl chloride
 (also known as vinyl), is a common plastic that frequently
 contains toxic additives.  Despite its well-publicized goal to
 "protect children's health," the Clinton administration is
 lobbying aggressively to avert a European ban on PVC toys.[1]

 At issue are a family of chemicals called phthalates (pronounced
 "thalates").  Phthalates (phthalic esters or benzenedicarboxylic
 acid esters) are used primarily as plasticizers added to PVC to
 make it soft and elastic.  Plasticizers account for more than
 half the weight of some flexible PVC products.   About 95% of
 phthalates are used in PVC.[2]

 Since they are not chemically bound to the PVC polymer itself,
 phthalates readily leach out of PVC products.  Up to 1% of the
 phthalate content of PVC products is released each year.[3]  As a
 result of their continuous release during the production, use and
 disposal of PVC products, phthalates are often described as the
 "most abundant man-made environmental pollutants." (See REHW
 #438).

 Although phthalates vary in toxicity, the most widely-used
 phthalates such as DEHP [di(2-ethylhexyl)phthalate] have been
 linked in animal studies to a variety of illnesses, including
 reproductive damage and damage to the kidneys and liver.[4]
 Several agencies, including U.S. EPA [Environmental Protection
 Agency], have labeled DEHP a probable human carcinogen.[4]  One
 recent study found a strong correlation between testicular cancer
 and exposure to PVC in workers who make PVC products. The authors
 of the study suspect that phthalates may play a role in their
 findings.[5]

 Other studies suggest that phthalates or their metabolites can
 interact synergistically with other common chemical
 contaminants,[6] may be slightly estrogenic[7] (which means they
 may play a role as endocrine disrupters), can affect blood
 pressure and heart rate,[8] and may cause asthma when absorbed on
 airborne particles.[9]

 The simple truth about phthalate toxicity is revealed by the
 warning label on a bottle of DINP, the phthalate most commonly
 found in toys. The label on a bottle of DINP sold to an
 experimental laboratory says, "May cause cancer; harmful by
 inhalation, in contact with skin, and if swallowed; possible risk
 of irreversible effects; avoid exposure; and wear suitable
 protective clothing, gloves, and eye/face protection."[10]  On
 the other hand, a typical PVC teething ring or bath duck
 containing about 40% by weight of DINP either has no label or
 carries a label that reads "Non-Toxic."

 Although no standard method exists for the investigation of
 release of phthalates from toys, a group of Danish scientists
 found significant migration of phthalates used in  toys.[11]
 Soon after, some of Denmark's biggest retailers took
 precautionary action by pulling a number of chewable PVC toys off
 theit shelves.  Since then, a number of retailers in Spain,
 Sweden Italy, Germany, the Netherlands and Belgium have stopped
 selling PVC teething toys.

 No major U.S. retailers have taken similar precautionary action,
 chiefly because the U.S. Consumer Product Safety Commission
 (CPSC), which is responsible for toy safety regulations, has yet
 to take a position.  In the mid-'80s, after the CPSC looked into
 the leaching of DEHP from teethers, the toy and chemical
 corporations deflected restrictions on the use of PVC by
 voluntarily substituting another phthalate for DEHP.

 When the EU was asked to restrict PVC toys, it called upon its
 own Scientific Committee, which investigated and then issued a
 report in April 1998.  The report acknowledged that the EU's
 assessment "did not take into account that more than one
 phthalate may occur in children's toys or that there may be
 additional exposures through food, air and by dermal contact to
 these phthalates."[12]  Nevertheless, the EU's Scientific
 Committee found that two common phthalate plasticizers used to
 make flexible toys (DINP and DEHP) leached from PVC toys at
 levels of concern.

 Phthalates migrate into food from plastic food wraps.  A recent
 survey of U.S. cheeses by CONSUMER REPORTS magazine found that
 phthalates and adipates (another PVC plasticizer) directly
 migrate from commercial PVC and PVDC plastic wrapping into
 cheeses.[13]  "In the cheeses [Consumer Reports] found:

 "...very heavy migration (50 to 160 parts per million) of the
 adipate plasticizer DEHA into cheeses in deli cling wrap.  People
 who ate several ounces of this cheese every day could get doses
 nearly as high as those linked to a host of health problems in
 lab animals.

 "...moderate migration (1 to 4 parts per million) of the most
 common phthalate, DEHP, into some of the  shrink-wrapped cheeses
 and into two waxed cheeses with clear plastic overwrap."

 The June CONSUMER REPORTS says, "It's impossible to say whether a
 tiny serving of plasticizers is risky.  If you want to play it
 safe, buy one of the wraps we found to be free of suspect
 plasticizers, or buy any polyethylene wrap."  A sensible
 recommendation that would help reduce exposure.

 The toy and PVC industries point to the use of PVC in medical
 devices to suggest that its use in toys and food wraps is safe.
 Yet phthalates DO leach from medical products, often resulting in
 high exposures to particularly vulnerable individuals, including
 people with suppressed immune systems, pregnant women, and
 children.  Estimates of exposure levels indicate that
 hemophiliacs may be exposed to 1 to 2 milligrams per day (mg/day)
 and dialysis patients may receive doses as high as 40 mg/day.  In
 one study, seven out of twelve samples of lung tissue, taken at
 autopsy from patients who had received transfusions of stored
 blood, contained DEHP at concentrations of 13.4 to 91.5
 milligrams per kilogram (mg/kg) (dry weight).[14]

 Preliminary evidence has linked illnesses to high levels of
 exposure to phthalates from medical devices.  For instance,
 unusual lung disorders were observed in pre-term infants
 artificially ventilated with PVC respiratory tubes.[15] Infants
 in neonatal intensive care units are regularly exposed to DEHP
 following blood transfusions or respiratory oxygenation.  As the
 authors of one study put it, "whether such exposure leads to
 increased morbidity is not known, although elevated levels of
 DEHP have been associated with necrotizing enterocolitis and
 cholestasis. There is no appropriate risk assessment for neonatal
 infants who are exposed to this compound."[16]

 While high levels of phthalates appear to be leaching from
 products such as medical devices, toys and packaging (products
 coming directly in contact with humans or food), these are just a
 small part of the widespread dispersion of phthalates into the
 environment.  The Swedish EPA estimates that "the greatest spread
 of phthalates should occur from the outside use of coated fabric
 and coated plating, and from (automobile) underseal compound.  As
 an estimate, these products are responsible for 90% of phthalate
 emissions..."[17] Other studies have shown that plasticizers are
 extracted from PVC flooring when it is washed and from textiles
 imprinted with PVC.[18]  Phthalates are also found in leachate
 from landfills (released from buried PVC).[19]

 Only a total phase-out of flexible PVC products can address the
 global spread of phthalates.  Such a large-scale phase-out is
 feasible because alternatives exist for nearly every use of
 PVC.[20]  In most cases, the alternatives are cost-effective.
 For instance, PVC-free intravenous solution bags are cheaper than
 PVC bags.[21]  The plastics industry is also developing a new
 generation of high-performance polyolefins (chlorine-free
 plastics such as polypropylene and polyethylene) which industry
 analysts contend will soon be cost competitive with PVC in
 applications "where the plasticizer cost has a significant impact
 on total end use cost" (for example, flexible PVC with phthalate
 additives).[22] None of these other plastics requires PVC's
 extensive use of toxic additives.

 Since PVC products are common, the immediate goal should be to
 change the composition of products that people (especially
 children) contact directly. Thus, banning PVC teething rings
 would set an important precautionary precedent. In May the
 government of Sweden proposed a ban on the use of phthalates in
 all toys for children under age 3.

 As cable traffic between the Department of Commerce and the U.S.
 EU delegation reveals, the U.S. has pressured the EU to not take
 any action until studies by the Consumer Product Safety
 Commission are completed.  A draft of the CPSC's report (which
 relies almost exclusively on data provided by phthalate
 manufacturers) concludes that DINP can be regarded as toxic under
 the Federal Hazardous Substances Act but additional information
 is needed on the release of DINP from children's products before
 the CPSC could recommend action.[23]

 Thus, although there is no standard testing procedure to measure
 phthalates released when children suck or chew on PVC toys, and
 though countries such as Denmark, and the EU's Scientific
 Committee, have concluded that phthalates leach from toys at
 levels of concern, more data are needed before the CPSC will make
 up its mind.

 Meanwhile, the nation's children are being used as guinea pigs.


 ===============

 [1] James Gerstenzang, "U.S. Urges European Union to Avert Toy
 Restrictions," LOS ANGELES TIMES, May 28, 1998, p. A1.

 [2] T.J. Wams, "Diethylhexylphthalate as an Environmental
 Contaminant--A Review," SCIENCE OF THE TOTAL ENVIRONMENT Vol. 66
 (October 1987), pgs. 1-16.

 [3] Cadogan, D.F. and others, AN ASSESSMENT OF THE RELEASE,
 OCCURRENCE AND POSSIBLE EFFECTS OF PLASTICIZERS IN THE
 ENVIRONMENT (Brussels, Belgium: European Council for Plasticisers
 and Intermediates, 1993).

 [4] Agency for Toxic Substances and Disease Registry,
 TOXICOLOGICAL PROFILE FOR DI (2-ETHYLHEXYL) PHTHALATE [TP-92/05]
 (Atlanta, Ga.: Agency for Toxic Substances and Disease Registry,
 April, 1993).

 [5] Lennart Hardell and others, "Occupational exposure to
 polyvinyl chloride as a risk factor for testicular cancer
 evaluated in a case-control study," INTERNATIONAL JOURNAL OF
 CANCER Vol. 73 (1997), pgs. 828-830.

 [6] M.G. Narotsky and others, "Nonadditive Developmental Toxicity
 in Mixtures of Trichloroethylene, Di(2-ethylhexyl) Phthalate
 [sic], and Heptachlor in a 5 X 5 X 5 Design," FUNDAMENTAL AND
 APPLIED TOXICOLOGY Vol. 27 (1995), pgs. 203-216.

 [7] Catherine A. Harris and others, "The Estrogenic Activity of
 Phthalate Esters IN VITRO," ENVIRONMENTAL HEALTH PERSPECTIVES
 Vol. 105, No. 8 (August 1997), pgs. 802-811.  And see Susan
 Jobling and others, "A Variety of Environmentally Persistent
 Chemicals, Including Some Phthalate Plasticizers, Are weakly
 Estrogenic," ENVIRONMENTAL HEALTH PERSPECTIVES Vol. 103, No. 6
 (June 1995), pgs. 582-587.

 [8] Gail Rock and others, "Hypotension and cardiac arrest in rats
 after infusion of mono(2-ethylhexyl)phthalate (MEHP), a
 contaminant of stored blood," NEW ENGLAND JOURNAL OF MEDICINE
 Vol. 316 (May 7, 1987), pgs. 1218-1219.

 [9] Leif Oie and others, "Residential Exposure to Plasticizers
 and Its Possible Role in the Pathogenesis of Asthma,"
 ENVIRONMENTAL HEALTH PERSPECTIVES Vol. 105, No. 9  (September
 1997), pgs. 972-978.

 [10] Matthew Wald, "Lead Content is Found High in Plastic Items,"
 NEW YORK TIMES, October 10, 1997, pg. unknown.  And see Joe Di
 Gangi, LEAD AND CADMIUM IN VINYL CHILDREN'S PRODUCTS (Washington,
 D.C.: Greenpeace, 1997). Available at
 <http://www.greenpeaceusa.org>.

 [11] K. Vinkelsoe and others, "Migration of Phthalates from
 Teethering [sic] Rings," Department for Environmental Chemistry,
 Danmarks Miljoundersogelser, Frederiksborgvej 399, 4000 Roskilde,
 Denmark. Telephone +45 4630 1200; fax: +45 4630 1114.  April 15,
 1997.

 [12] PHTHALATES IN TOYS, OPINION OF THE EU SCIENTIFIC COMMITTEE
 ON TOXICITY, ECOTOXICITY AND THE ENVIRONMENT (Brussels, Belgium:
 European Union, April 24, 1998).

 [13] "Hormone Mimics: They're in our food; should we worry?"
 CONSUMER REPORTS, June, 1998, pg. 52-55. See also, J.H. Petersen
 and others, "PVC cling film in contact with cheese: health
 aspects related to global migration and specific migration of
 DEHA," FOOD ADDITIVES AND CONTAMINANTS Vol. 12, No. 2 (March
 1995), pgs. 245-253.

 [14] Charlotte Nilsson, editor, PHTHALIC ACID ESTERS USED AS
 PLASTIC ADDITIVES, VOLUME 2: COMPARISON OF TOXICOLOGICAL EFFECTS
 [No. 12/94] (Solna, Sweden: Swedish National Chemicals
 Inspectorate, 1995[?]).  See <www.kemi.se>.

 [15] B. Roth and others, "Di-(2-ethylhexyl)-pththalate as
 plasticizer in PVC respiratory tubing systems: indications of
 hazardous effects on pulmonary function in mechanically
 ventilated, preterm infants," EUROPEAN JOURNAL OF PEDIATRICS Vol.
 147 (1988), pgs. 41-46.

 [16] S.L. Plonait and others, "Exposure of newborn infants to
 di-(2-ethylhexyl)-phthalate and 2-ethylhexanoic acid following
 exchange transfusion with polyvinylchloride catheters,"
 TRANSFUSION Vol. 33, No. 7 (1993), pgs. 598-605.

 [17] Swedish National Chemicals Inspectorate, ADDITIVES IN PVC;
 MARKING OF PVC; REPORT ON COMPLETION OF A GOVERNMENT TASK (Solna,
 Sweden: Swedish National Chemicals Inspectorate, June 28, 1996

 [18] J. Vikelsoe and E. Johansen, "Phthalates emitted when
 washing floors and textiles containing PVC."  Place of
 publication and publisher unknown.  Cited in Swedish National
 Chemicals Inspectorate, ADDITIVES IN PVC; MARKING OF PVC; REPORT
 ON COMPLETION OF A GOVERNMENT TASK (Solna, Sweden: Swedish
 National Chemicals Inspectorate, June 28, 1996.

 [19] Danish Technological Institut [sic], ENVIRONMENTAL ASPECTS
 OF PVC (Copenhagen, Denmark: Danish Technological Institut,
 November 1995), pg. 91.

 [20] See, for example, Danish Technical Institute, PVC AND
 ALTERNATIVE MATERIALS [Ministry of the Environment Report
 18/1993] (Copenhagen: Ministry of the Environment, Danish
 Environmental Protection Agency [Strandgade 29, DK-1401
 Copenhagen, Denmark], 1993.

 [21] Conversation with Dan Rice, Midwest Sales Representative,
 McGaw, Inc., April 1997.  Telephone: (800) 345-7744 ext. 4230 or
 773-693-2170.

 [22] Robert B. Wilson, SRI International, "The Impact of
 Metallocenes on PVC," unpublished paper presented at the World
 Vinyl Forum, September 1997.  SRI International, 333 Ravenswood
 Avenue, Menlo Park, CA 94025.  Telephone (650) 326-6200.

 [23] Memorandum from Michael A. Babich, Ph.D., Chemist, Division
 of Health Sciences, U.S. Consumer Product Safety Commission, to
 Ronald L. Medford, Assistant Executive Director for Hazard
 Identification and Reduction, March 10 1998.


 Descriptor terms:  pvc; polyvinyl chloride; vinyl; plastics;
 carcinogens; di(2-ethylhexyl)phthalate; dehp; adipate;
 plasticizers; deha; food safety; consumer product safety
 commission; cpsc; toys; children; blood; phthalates; european
 union; eu; hazardous substances act; testicular cancer;


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 from:
             RACHEL'S ENVIRONMENT & HEALTH WEEKLY #609
                        ---July 30, 1998---

 CORRECTION

 Consumers Union (CU) did not test cheeses wrapped in PVDC food
 wrapping as reported in REHW #603. CU tested for plasticizers in
 cheese wrapped in PVC food wrapping. Although the wraps contained
 no phthalate plasticizers (phthalates found in the cheese are
 apparently from another source), CU did find high levels of
 adipates, a related group of plasticizers, as we reported.
 Details of Consumer's Union's tests can be viewed at
 <www.consunion.org>.

 =================================================================

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