Beauty Secrets

Environmental Working Group Nov00

Researchers Warn Consumers About Hazardous Ingredient In Nail Polish

Growing Scientific Concern About Dibutyl Phthalate (DBP), Reproductive Age Women and Links to Birth Defects

Executive Summary

Contents

Source: http://www.ewg.org/pub/home/reports/beautysecrets/pr.html

Environmental Working Group
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In September 2000, researchers at the Centers for Disease Control and Prevention (CDC) reported that every single one of the 289 persons tested for the plasticizer dibutyl phthalate (DBP) had the compound in their bodies. The finding passed with little public fanfare, but surprised government scientists, who just one month earlier had rated DBP of little health concern based on the scientific assumption, which later turned out to be wrong, that levels in humans were within safe limits. DBP causes a number of birth defects in lab animals, primarily to male offspring, including testicular atrophy, reduced sperm count, and defects in the structure of the penis (CERHR 2000).

The most critical population, women of childbearing age whose fetuses are exposed in the womb, appear to receive the highest exposures. Estimates based on data published by the same CDC researchers in October 2000, indicate that DBP exposures for 3 million women of childbearing age may be up to 20 times greater than for the average person in the population. The highest exposure estimates for these women were above the federal safety standard (Blount et al 2000, Kohn et al 2000, EPA 1990). EPA rates their overall confidence in the safety standard as "low", largely because it is based on a study published in 1953 that did not examine the test animals for the birth defects that concern scientists today (EPA 1990).

DBP is just one ingredient in an alphabet soup of pollutants that contaminate every person in the industrialized world. A patchwork of studies from the federal government indicates that everyone in the United States carries more than 100 chemical pollutants, pesticides, and toxic metals in their bodies. No one knows exactly where these exposures come from, and no one has studied the effect of constant exposure to this low-level mixture of poisons. Nor is it possible to do so. To test 100 chemicals in combinations of three for just one health effect (cancer, for example, as opposed to birth defects) would require 162,000 new tests. There are currently 75,000 chemicals licensed for use in the United States. Approximately 15,000 are sold in volumes greater than 10,000 pounds per year. Under the Toxic Substances Control Act the EPA has regulated just five chemicals (Roe et al 1997).

Government researchers speculate that the elevated levels of DBP among women of childbearing age come from cosmetics and beauty products, but no one has done the studies to test this hypothesis. As a first step in discovering some major sources, the Environmental Working Group (EWG) shopped at a local Rite-Aid, surfed the on-line store Drugstore.com, and searched the U.S. patent office records for products that contain DBP in the patent application. We found:

DBP in 37 popular nail polishes, top coats, and hardeners, including products by L'Oréal, Maybelline, Oil of Olay, and CoverGirl (Table 1).


Chemical industry systematically defeats health protections

No pre-market safety testing or approval is required under any federal law for chemicals in cosmetics, toys, clothing, carpets, or construction materials, to name just a few obvious sources of chemical exposure in everyday life. This little known fact is the premeditated result of an orchestrated campaign by the chemical industry to avoid testing and regulation of their products. It largely explains why products like hair spray, hair dye, pacifiers, stain repellants, glues and children's toys get on the market, only to be found to contain highly toxic compounds at unsafe levels after decades of widespread use. Once these products are on the market, there is no practical legal mechanism by which health authorities can remove them from commerce, short of a public health disaster or consumer uproar.

OSHA

Since the 1950's, the chemical industry has systematically blocked efforts to require safety studies for the compounds it produces. This strategy first played out with workplace standards adopted under the Occupational Safety and Health Administration (OSHA), and was repeated with the passage and implementation of the Toxic Substances Control Act (TSCA).

The first chemical health standards in the United States were adopted by OSHA in 1972. Set in theory to protect workers, these standards were initially created in the 1940's by representatives from the chemical industry operating under the auspices of the American Council of Governmental and Industrial Hygienists (ACGIH). At the time the standards were first introduced in 1942, ACGIH issued major caveats regarding their application to human health, stating that: "[they are] not to be construed as recommended safe concentrations" (NCGIH 1942).

Toxicity tests on animals had barely been invented at that time, and the standards themselves were based on rough estimates of acutely hazardous and lethal levels of exposure. In the words of the scientist who devised many of them, the so-called threshold limit values (TLVs) were designed, "to provide a handy yardstick to be used as guidance for the routine control of these health hazards - not that compliance with the figures listed would guarantee protection against ill health" (Cook, 1945).

This did not stop the chemical industry from promoting TLVs as legitimate health standards, and in 1972, OSHA adopted TLVs wholesale as the nation's first set of enforceable health standards for chemicals in the workplace. In the process these "handy yardsticks" took on an aura of respectability that belied the fact that there was essentially no science to support their relevance to human health and safety. The best estimates are that basic toxicological data were available for only five percent of some 600 industrial chemicals for which OSHA had adopted standards by 1988 (Castleman and Ziem 1994, Roach and Rappaport 1990).

TSCA

This process of faux regulation was repeated again when the same chemical industry giants teamed up to write the nation's major toxic chemical law, the Toxic Substances Control Act (TSCA). Passed with virtually no regulatory teeth, TSCA has been an unparalleled failure. Of the 62,000 chemicals on the market when TSCA was passed in 1976, EPA has successfully requested data for 263 compounds. Of the 15,000 chemicals marketed in quantities exceeding 10,000 pounds per year, EPA has completed regulatory actions to limit use or exposures on just 5, or 0.03 percent (3 one hundredths of one percent). Four of the five were already regulated under other statutes, and only one, lead in paint, affected a consumer product (Roe et al 1997).

TSCA is best thought of as a self-defeating feedback loop. Under the law, all chemicals are presumed safe, and the burden of proof is on the EPA to demonstrate that a chemical is causing harm before it can take any regulatory action. However, the agency cannot require that industry conduct the tests needed to show that a chemical is causing harm, until the agency has shown that the compound may present an "unreasonable risk," or that human exposure is "substantial" or "significant". Substantial exposures can almost never be proven without additional data from industry, and significant exposures cannot be proven without information on the chemical's toxicity. Of course, compelling toxicity data are almost never available for the compound in question or EPA would not be trying to publish a test rule in the first place.

Even if all these hurdles are cleared, which is extremely unlikely, in order to request basic toxicity data on any single chemical the EPA must issue a test rule through the process of a rulemaking under administrative law. This roadblock is unique to TSCA. Under pesticide law, or food safety law, EPA or FDA can request virtually any test that they need to assess the safety of a compound.

A defining moment in the collapse of TSCA occurred in 1990 when EPA attempted to issue test rules for the paint thinner cumene. The proposed test rules were immediately challenged by the Chemical Manufacturers Association on the grounds that EPA had not shown that human exposure was "substantial," the basic requirement under Section 4 of the Act. The courts upheld the CMA argument that the burden of proving "substantial" exposure and risk was on the EPA and not the manufacturers (Chemical Manufacturers Ass'n v. EPA, 5th Cir. 1990).

To date EPA has issued rules requiring toxicity testing for 0.4 percent, or 263, of the 62,000 chemicals on the market when the law was passed. And even when issued, test rules generally do not require comprehensive testing. With barely any data generated via test rules the agency cannot support a finding of substantial risk for any chemical, and indeed the agency has taken only five final actions since passage of the law (Roe et al 1997).

The final nail in the coffin came in 1991. EPA was trying to use TSCA to regulate asbestos, arguing that it presented an "unreasonable risk of injury" to human health. Again the TSCA feedback loop prevailed, and the court ruled that EPA had not met the burden of providing substantial evidence that asbestos presented an unreasonable risk of injury to human health (Corrosion Proof Fittings v. EPA, 5th Cir. 1991). Since this decision, EPA has undertaken no additional major regulatory actions under the Act.

Under pressure from environmentalists and the Clinton administration, in 1999 the chemical industry agreed to conduct basic health screening tests for about 3,000 high production volume compounds out of a universe of more than 75,000 chemicals registered for commercial use today, 15,000 of which are marketed in quantities exceeding 10,000 pounds per year. This tiny step forward is entirely voluntary and, even if it is completed, it will not provide regulators and public health authorities with sufficient information to fully assess the long-term adverse effects of toxic chemical exposure. Tests now recognized as critical to a full understanding of a chemical's toxicity will not be conducted at all under this initiative. These include cancer bioassays, studies on the developing nervous system, the immune system, the endocrine system, and perhaps most important, human monitoring to determine the extent of human exposure.

This latter element is critical. As discussed below, a string of recent discoveries reveal that human exposure to commercial chemicals used in common consumer products is almost certainly much more pervasive than previously thought. This new strata of contamination is in addition to the considerable well-known toxic load of pollutants (such as PCBs, dioxin, and DDT) found in the blood and body fat of virtually all people in the industrialized world.


Phthalates

Invented in the 1930's, the versatile group of common industrial chemicals called phthalates (pronounced tha-lates) are used as ingredients in a diverse range of consumer products from cosmetics to food wraps, toys and building materials. Currently the chemical industry produces billions of pounds of phthalates each year. They are used as plasticizers to soften plastic, as skin moisturizers and skin penetration enhancers in cosmetics, and as solvents in a wide range of applications. People are exposed to phthalates daily through their contact with consumer products and via food and indoor air.

In spite of their widespread presence in cosmetics and other common consumer products, industry has only partially studied the health effects of phthalates and has never tested for the presence of phthalates in human bodies. Finally, in April 1999, over six decades after phthalates were first marketed, the federal government's National Institute for Environmental Health Sciences (NIEHS) initiated a study of the effects of phthalates on the human reproductive system through their new Center for the Evaluation of Risk to Human Reproduction (CERHR).

At the same time, scientists at the Centers for Disease Control and Prevention (CDC) were achieving the first accurate measurements of phthalates in people. Researchers there were surprised to find that people have much higher levels of some phthalates in their bodies than predicted by previous estimates (Blount et al 2000). In October 2000, CDC scientists announced that levels of some phthalates in women of childbearing age, including dibutyl phthalate (DBP) and di(2-ethylhexyl) phthalate (DEHP), exceed the government's safe levels set to protect against birth defects. Estimates based on data from this study indicate that for more than 3 million heavily exposed women of childbearing age, exposures to DBP may be 20 times greater than the average exposures in the rest of the population (Kohn et al 2000).

This report focuses primarily on DBP, a widely used phthalate that produces serious reproductive and developmental effects in laboratory animals. But DBP is not the only toxic phthalate to which people are routinely exposed. Many other phthalates widely detected in human urine by the CDC cause the same birth and developmental defects to the male reproductive system as DBP. Absent evidence to the contrary, it is reasonable to assume that the health effects from exposures to multiple phthalates are additive.

Health effects of dibutyl phthalate

At least two decades ago, scientists began building a body of work indicating that DBP can be a powerful reproductive and developmental toxicant in laboratory animals, particularly for males. Early studies focused on DBP's ability to cause testicular atrophy (e.g., Gray et al 1980), but DBP is now known to cause a broad range of birth defects and lifelong reproductive impairment in male laboratory animals exposed in-utero and shortly after birth (Ema et al 1998, Marsman et al 1995, Mylchreest et al 1998, 1999, and 2000, Gray et al 1999, Wine et al 1997 ).

Scientists believe that the active toxicant of DBP exposure is its first breakdown product, monobutyl phthalate (MBuP), which has been shown to harm the male reproductive system. The precise mechanism of action is not known but the pattern of reproductive harm is consistent with other so-called anti-androgens or chemicals that interfere with the male hormones called androgens.

Effects in immature male animals: DBP exposure damages the testes, prostate gland, epididymus, penis, and seminal vesicles in laboratory animals (see, for example, Mylchreest et al, 1998). These effects persist throughout the animal's life, and include, specifically:

Testicular atrophy (the testes produce sperm and male sex hormones)

 

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