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Toxic Chemicals in Toys and Children's Products: Limitations of Current Responses and Recommendations for Government and Industry

Authors:
  • Monica Becker & Associates

Abstract

Hazardous substances in consumer products are a constant worry. Because children have less body mass and are developing rapidly, toxic chemicals in toys are of particular concern. Recent studies have revealed alarming levels of cadmium and lead in products intended for children and compounds in plastics, such as phthalates and bisphenol A, that are suspected of harmful effects. As Europe has introduced REACH and the U.S. is reviewing TSCA, regulators are confronting the issue, but an increasing global market poses problems of jurisdictional reach and supply chain management. In this Feature, Becker et al. review the situation and make recommendations on ways forward.
Toxic Chemicals in Toys and
Children’s Products: Limitations of
Current Responses and
Recommendations for Government
and Industry
MONICA BECKER*
Monica Becker & Associates Sustainability Consultants,
Rochester, New York
SALLY EDWARDS
Lowell Center for Sustainable Production, University of
Massachusetts, Lowell, Massachusetts
RACHEL I. MASSEY
Massachusetts Toxics Use Reduction Institute, University of
Massachusetts, Lowell, Massachusetts
Introduction
In June 2007, RC2 Corporation, manufacturer of a popular
line of brightly painted wooden trains, recalled more than
1.5 million units after learning that they violated the U.S.
government standard for lead (Pb) in paint. The U.S.
Consumer Product Safety Commission (CPSC) warned
parents that children should stop using the toys immediately
(1). This was not an isolated incident; in 2007, over 17 million
toys were recalled because they violated the federal Pb paint
standard (2). In January 2010, the CPSC recalled 55,000 units
of children’s costume jewelry that contained high levels of
cadmium (Cd) (3). In June 2010, 12 million promotional
drinking glasses sold at McDonald’s were recalled because
the painted coating contained Cd (4). Again, consumers were
advised to stop using the product immediately.
The 2007 recalls brought attention to the problem of toxic
chemicals in toys and other children’s products and the 2010
recalls have been a reminder that this problem is yet to be
solved. While violations of existing regulatory standards may
have garnered the most press attention, they are merely the
tip of the iceberg: for many other toxic chemicals, no
regulatory standards are in place.
Since 2007, a variety of activities have been undertaken
to address the problem of toxic chemicals in toys and
children’s products. Government responses include regula-
tory measures to increase companies’ accountability, re-
strictions on the use of certain toxic chemicals, and disclosure
requirements. Nonprofit sector efforts are aimed at providing
information to consumers, advocacy to support broad
legislative reform, and development of an eco-label certi-
fication program for toys. The toy industry in the U.S. has
focused primarily on developing a conformity assessment
system to ensure that toys comply with existing U.S.
regulations and standards.
While these initiatives are positive developments, much
of the response to the “toxic toys” crisis has been reactive
and piecemeal. Taken as a whole, these responses have not
been sufficient to ensure that toys and children’s products
are safe. This article reviews recent efforts to address toxic
chemicals in toys and offers recommendations for further
action by government and industry.
Why toxic chemicals in toys are a serious concern
Toxic exposures in children are a significant concern because
of a number of factors, including a higher metabolic rate and
greater surface area to weight ratio than adults, immaturity
of organ systems, and rapid growth and development of
organs and tissues such as bone and brain. Children’s
exposure also differs from that of adults because children
drink more fluids, eat more food, and breathe more air per
kilogram of body weight. Children also have many years ahead
to develop diseases with long latency periods (5). Young
children’s frequent hand to mouth activity creates a pathway
for toxic chemicals in toys and other products to enter the
body. Children receive multiple low dose exposures daily
from a variety of products with which they come into contact,
in addition to chemicals in household dust and the outdoor
environment.
Table 1 lists some of the toxic chemicals found in toys
and children’s products, describes exposure pathways, and
includes the current status of U.S. federal regulations.
Toys and other products intended specifically for children
are one category of a much larger set of consumer products
that expose infants and children to toxic chemicals, such as
personal care products, furniture, and food containers. This
article focuses on toys and other children’s products because
they are specifically intended for this vulnerable population.
Why are there toxic chemicals in toys?
There are two major reasons why toys contain toxic chemicals:
lack of regulation and violation of existing regulations. This
ANN BLAKE
Environ. Sci. Technol. 2010, 44, 7986–7991
7986 9ENVIRONMENTAL SCIENCE & TECHNOLOGY / VOL. 44, NO. 21, 2010 10.1021/es1009407 2010 American Chemical Society
Published on Web 09/27/2010
latter problem results in part from the complexity of global
production systems.
Regulatory gaps. The U.S. Environmental Protection
Agency (EPA) lists over 80,000 chemicals in its Toxic
Substances Control Act (TSCA) inventory, but few have been
adequately tested for safety (10). Under TSCA, extensive
hazard and exposure data are needed before EPA can act to
restrict the use of chemicals. Historically, even when the link
between exposure to a chemical and illness or injury is well
documented, EPA has done little to restrict its use (11). It is
widely recognized that TSCA is outdated and EPA and
advocacy groups are pressing for legislative reform (12). Other
federal agencies are also increasingly concerned about toxic
chemicals in the environment (13).
In principle, the CPSC has the authority to regulate
toxic chemicals in products, but in practice the CPSC’s
reach has been limited (14). Under the Federal Hazardous
Substances Act (FHSA), the presence of a toxic substance
in a product is not a sufficient condition for labeling or
banning the substance. FHSA requires application of a
risk-based determination of “substantial personal injury
or substantial illness” resulting from exposure (15).
Companies are responsible for making this determination,
using general guidelines provided by CPSC but are not
compelled to generate the relevant exposure and dose-
response information that would form the basis for such
a determination.
With regard to toys specifically, safety requirements in
the U.S. and other industrialized countries have focused
primarily on mechanical safety such as preventing choking,
laceration, or other injuries. As choking hazards remain a
leading cause of toy-related injuries, this is an important
area of continued focus (16). Until recently, there has been
little focus on chemicals in toys. Under current regulations,
the CPSC restricts just fourteen chemicals in toys, including
eight heavy metals and six phthalates (17).
TABLE 1.Examples of Toxic Substances in Toys and Other Children’s Products
VOL. 44, NO. 21, 2010 / ENVIRONMENTAL SCIENCE & TECHNOLOGY 97987
Why is cadmium in children’s jewelry?
In early 2010, researchers found high levels of Cd in popular
costume jewelry intended for children. The CPSC issued a
strong message advising parents to remove the product from
children to prevent harm (18). When the news became public,
some large retailers reacted quickly and removed these items
from their inventories.
Both changes in international markets and regulatory gaps
contributed to this situation. Until 2008, 75% of Cd produced in
China had been used for manufacturing nickel-cadmium
(NiCd) batteries (19). In September 2008, EU legislation
restricting the use of Cd in batteries came into force. The
Chinese government eliminated tax rebates for Cd batteries,
causing financial difficulties for exporters (20). As demand for
NiCd batteries dropped, the price of Cd decreased.
With the regulatory spotlight on lead in children’s products,
some manufacturers turned to cadmium as a substitute. There
are no U.S. federal regulations that that limit the use of this
toxic metal in children’s jewelry or require labeling of products
containing Cd. The CPSC currently limits cadmium in children’s
toys to 75 ppm and is working on new rules to limit the metal’s
presence in all children’s products, including jewelry.
Complex global supply chains. Toy production and
consumption occur in a global system characterized by large,
complex supply chains with constant downward pressure
on prices. In many cases, product design and marketing occur
primarily in developed countries, with manufacturing out-
sourced overseas. Demand for low cost products creates
pressure for companies to externalize environmental and
social costs, resulting in unsafe working conditions, envi-
ronmental pollution, and a drive toward using the cheapest
and often toxic materials.
Even when regulations are in place, a lapse in supply
chain management can lead to problems on a large scale.
For example, Mattel, the largest toy company in the world,
recalled over 2 million toys in 2007 for violation of the U.S.
Pb paint standard (21). In its investigation, Mattel discovered
that several contractors had purchased leaded paint from
suppliers that had not been certified by Mattel (22). Leaded
paint, used widely in China for industrial applications, is up
to one-third less expensive than nonleaded paint (23).
Responses to toxic chemicals in children’s products
1. Regulatory responses. Following the well-publicized
recalls of 2007, public demand for stronger assurance of toy
safety led to the enactment of the 2008 U.S. Consumer
Product Safety Improvement Act (CPSIA). The law amended
the outdated Consumer Product Safety Act of 1972. The CPSIA
significantly increases CPSC funding and enforcement
authority. It requires manufacturers to put tracking labels
on children’s products including information about the
manufacturer, production date, and batch to make it easier
to track unsafe products to their sources; makes mandatory
the requirements of the American Society for Testing and
Materials toy safety standard (ASTM F963) (24) and requires
that testing of children’s products be conducted by accredited
third-party laboratories (25).
Yet the CPSIA authority to address toxic chemicals in toys
is still quite limited. While it sets stricter standards for Pb
and restricts six phthalates in children’s products, it does
not address the larger universe of unregulated or under-
regulated chemicals in children’s products (26).
The EPA has recently stepped up its efforts to address the
problem of toxic chemicals in commerce and some of these
efforts may have implications for toxic chemicals in children’s
products. Among other activities, the agency has developed
action plans for a number of chemicals, outlining future
regulatory action (27). For example, EPA’s Phthalates Action
Plan notes concern about children’s exposure and identifies
this as an area for further study and regulatory action (28).
The EU recently overhauled its 20-year-old Toy Safety
Directive. In contrast to the CPSIA, the Directive takes a more
comprehensive approach to addressing toxic chemicals in
toys, prohibiting carcinogens, mutagens, and reproductive
toxicants (CMRs) in toys. It also sets new limits for 19
substances, some of which were not previously regulated,
and limits the use of allergenic fragrances. The EU Directive
requires manufacturers to conduct a safety assessment for
each toy before it is placed on the market, including an
analysis of chemical hazards that the toy may present and
an assessment of potential exposure to such hazards. Every
toy must bear a marking indicating that it meets these
requirements (29).
European consumer advocates are concerned that certain
provisions in the law will allow manufacturers to continue
to use toxic materials in toys (30). The revised Directive allows
manufacturers to self-certify, rather than requiring third-
party certification of toys. In addition, while the law prohibits
CMRs in toys, exemptions will be granted if these substances
are inaccessible to children; no suitable alternative exists; or
a scientific committee determines that the use is safe.
Companies manufacturing and selling toys in Europe are
also subject to the EU’s comprehensive chemicals policy
known as REACH (Registration, Evaluation, and Authorization
of Chemicals). Under REACH, companies must disclose the
presence of chemicals in their products if the European
Chemicals Agency has identified and included the chemicals
on its “Candidate List” of “Substances of Very High Concern”
and if the chemicals are present in a product at a level above
0.1 wt % (31). To date, 38 chemicals are on this list, with
more expected to be added over time (32).
In the U.S., a number of state governments have adopted
legislation to ban specific chemicals of concern, such as lead,
phthalates, and bisphenol A (BPA), in children’s products,
and to increase transparency about the presence of toxic
chemicals in these products. For example, Maine and
Washington adopted legislation in 2008 that, among other
provisions, requires companies to submit data to the state
on toxic chemicals in children’s products (33, 34). These laws
require each state to create a list of chemicals of high concern.
Maine has listed 1700 chemicals of high concern based on
their inherent hazard; this list will be narrowed to identify
priority chemicals based on potential exposure. Manufactur-
ers will be required to disclose to the state their use of priority
chemicals. In June 2010, Maine proposed designating BPA
as a priority chemical. Washington recently issued a draft list
of 66 priority chemicals (35).
In addition, some state governments are beginning to
require industry to conduct assessments to identify safer
alternatives to chemicals of concern for specific applications.
Under Maine’s legislation, a manufacturer or distributor of
a children’s product that contains a priority chemical may
be required to conduct an alternatives assessment. Draft
regulations being developed by California’s Department of
Toxic Substances Control Authority would also require
companies using a chemical of concern in certain product
categories to conduct an alternatives assessment (36). To
support these and related efforts, the Toxics Use Reduction
Institute at the University of Massachusetts Lowell is leading
a multistate initiative to develop consistent methodologies
for assessing alternatives to toxic chemicals (37).
Prior to this new wave of legislative efforts, some states
already had programs in place to increase transparency about
toxic chemicals in consumer products, including toys.
California’s Safe Drinking Water and Toxic Enforcement Act
7988 9ENVIRONMENTAL SCIENCE & TECHNOLOGY / VOL. 44, NO. 21, 2010
of 1986, more commonly known as Proposition 65, requires
businesses to notify consumers when a product contains
any chemical that is “known to the state of California to
cause cancer or reproductive toxicity (38).” Eight states
require companies selling mercury (Hg)-added products to
submit detailed product information to a centralized database
(39).
Finally, efforts to gain more information about toxic
chemicals in toys may benefit from a new project, led by the
United Nations Environment Program (UNEP) under the
Strategic Approach to International Chemicals Management
(SAICM), to form a harmonized international information
system on chemicals in products. In 2009, UNEP conducted
a global survey of stakeholders and identified toys and
children’s products as a high priority sector for UNEP’s
continued work (40).
2. Nongovernmental responses. Since 2007, two U.S.
organizations have worked to fill information gaps by creating
web-based systems to give consumers information on
chemicals in toys and other products. The Michigan-based
Ecology Center (41) tests toys and other consumer products
for the presence of six chemicals that can be detected with
an X-ray fluorescence (XRF) sensor: Pb, Cd, chlorine (Cl),
arsenic (As), bromine (Br), and Hg. The database provides
a rating (high, medium, or low concern) for each product.
GoodGuide provides information on the environmental,
social, and health performance of products and companies
by integrating information from a variety of data sources.
GoodGuide provides information on more than 65,000
products, including toys, food, and household and personal
care products. It provides both a summary score for health/
social/environmental attributes and individual scores so that
consumers can focus on a particular attribute (42).
In 2009, EcoLogo, an environmental certification orga-
nization, launched a public stakeholder process to develop
an eco-label for toys (43). This standard, to be finalized by
December 2010, will consider the entire product life cycle in
determining criteria for safe, healthy, and environmentally
sustainable toys. These criteria will provide valuable design
guidance for manufacturers that choose to lead in this arena.
3. Industry responses. The leading U.S. trade group for
toy manufacturers, the Toy Industry Association, has created
the Toy Safety Certification Program, designed to ensure that
toys sold in the U.S. conform to the requirements of the
CPSIA and the toy safety standard, ASTM F963. This program
is valuable to manufacturers as it provides a consistent
evaluation method and is designed to minimize testing costs.
It requires a hazard/risk analysis in the design stage, factory
audits, and production sample testing. However, it does not
go beyond ensuring compliance with existing safety standards.
Some small and medium-sized toy companies are taking
leadership in developing environmentally sustainable toys.
The Eco-Toy Alliance, a partnership of four small toy
companies, has created a Web site to educate consumers
about the attributes of eco-friendly toys and market their
products (44). This may signify a trend among smaller and
start-up companies to use green product features to their
strategic advantage. In February 2010, the New York Toy
Fair, one of the world’s largest toy trade shows, included an
“earth-friendly product zone” for the first time.
The company World Environmental Regulatory Compli-
ance Solutions (The WERCS) has developed a tool called the
GreenWERCS Chemical Screening Tool that evaluates chemi-
cal products such as paints and cleaning products for human
and environmental health risks and scores products on this
basis. The WERCS keeps formulation data confidential but
provides retailers with information on chemical hazards. In
principle, retailers can use this information to compare
competing products and encourage suppliers to substitute
safer ingredients for harmful ones (45). Although the Green-
WERCS tool is not currently used for toys, this approach
could be applied to children’s products. Business-to-business
transparency initiatives may prove to be powerful drivers of
change if retailers use this information to select greener
products and motivate their suppliers to redesign products.
Some large retailers are working with suppliers to define
design elements for eco-friendly toys and in some cases to
create private label products that meet these criteria. For
example, in March 2008 Toys R Us announced a new line of
eco-friendly toys, including those made with FSC certified
wood and organic cotton (46). While it is not clear how
retailers enforce requirements, these actions signal the
potential power of the retail sector to drive market changes.
Recommendations for government and industry
What does the U.S. government need to do? New regulations
on individual chemicals have had some effect on toys sold
in the U.S. CPSC recalls for Pb in toys have decreased
significantly, from over 17 million units in 2007, to 1.3 million
in 2008, to approximately 110,000 in 2009 (47). However,
eliminating toxic chemicals in children’s products is still a
distant goal.
With over 80,000 chemicals in commerce, it is clear that
a chemical-by-chemical regulatory approach cannot solve
the problem. A solution will require significant policy changes
(48). Four key elements should be part of these improvements.
1. Ban or restrict the use of chemicals with well-
documented toxicity in toys and other children’s products. At
a minimum, these include persistent, bioaccumulative, and
toxic chemicals (PBTs), carcinogens, mutagens, and repro-
ductive toxicants (CMRs), neurotoxicants, and endocrine
disruptors. To be effective and avoid unintended conse-
quences, such restrictions must delineate categories of
chemicals rather than simply regulating individual toxic
chemicals. The EU’s approach to CMRs in the Toy Safety
Directive may provide a model.
2. Ensure consumers’ “right to know” about toxic chemicals
in children’s products. The federal government should develop
requirements for labeling products with information about
toxic constituents, as well as submission of data to centralized
databases.
In addition to empowering consumers to protect them-
selves, transparency changes the marketplace. Transparency
requirements can motivate manufacturers to change their
practices to avoid embarrassing disclosures and maintain
market share (49). For example, California’s Proposition 65
has motivated many companies to reformulate or redesign
products to eliminate or reduce the presence of a toxic
chemical (50, 51).
3. Require chemical manufacturers to generate and dis-
close basic toxicity information for all chemicals. Responsi-
bility for demonstrating the safety of chemicals should rest
with chemical manufacturers, rather than government.
Application of this principle is needed to improve the safety
of children’s products and consumer products in general
and is at the core of the EU’s REACH legislation. Current
work to implement these new requirements in the EU can
serve as a head start for industry and regulators in the U.S.
The Toxic Chemicals Safety Act, introduced in Congress in
July 2010, includes a requirement for disclosure of chemical
ingredients, with protection of confidential business infor-
mation (52).
4. Promote the design and development of safer children’s
products. The federal government should provide incentives
to encourage manufacturers to develop safer chemicals,
materials, and products, by increasing its support of green
chemistry and green design research and development in
industry and academia. The EPA’s Green Chemistry and
Design for Environment programs should be expanded. In
addition, the federal government should actively support
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the work of states that are working to develop consistent
methodologies for alternatives assessment of chemicals.
What does the toy industry need to do? In parallel with
efforts by government to improve regulation of chemicals in
toys, there are significant opportunities for the toy industry
to take proactive measures.
1. Identify chemicals of concern and establish robust
systems to test for these chemicals. One important step forward
for the toy industry would be to develop a list of chemicals
of concern that are found in children’s products. This
information would enable the toy sector to be proactive in
eliminating these chemicals where safer alternatives are
available, and jointly to pursue research on safer substitutes
where alternatives do not yet exist. Many other sectors,
including electronics, apparel (53), and automotive (54), have
worked together to develop lists of substances of concern,
and have created systems for improving information flow
about chemicals throughout their large and complex global
supply chains.
2. Engage openly with stakeholders. It would be useful
for the industry to interact more directly with all of its
stakeholders, including children’s environmental health
advocates, to address concerns about toxic chemicals. One
avenue for this engagement would be participation in the
Business-NGO Working Group, a collaboration of business
leaders from leading companies and nongovernmental
organizations that are working together to encourage the
use of safer chemicals in consumer products (55). This group
is convened by the nonprofit organization Clean Production
Action. The Green Chemistry and Commerce Council, a
network of some 100 firms and other organizations com-
mitted to developing safer chemicals and materials, convened
by the Lowell Center for Sustainable Production at the
University of Massachusetts Lowell, is another valuable
resource (56).
3. Develop a sustainability roadmap. The toy industry
should develop a roadmap for the development of sustainable
children’s products. Eliminating hazardous chemicals from
children’s products, while a critical goal, does not ensure
that these products are safe, healthy, and environmentally
sound throughout their life cycles. Numerous reports pub-
lished over the past decade by advocacy groups and industry
auditing organizations have documented unhealthy and
hazardous working conditions in toy factories (57, 58).
As a place to start, the toy industry can use the criteria
being developed by environmental certification organizations
to encourage companies to design and manufacture safer
and greener products. Additional tools and resources are
also available (59). For example, the Lowell Center for
Sustainable Production has developed a tool for product
designers and manufacturers to help evaluate environmental,
social, and economic impacts of existing products and to
design new products that minimize these impacts (60). This
framework can be used to redesign products and production
systems in advance of new regulations.
The road ahead
Concern over the problem of toxic chemicals in toys is
growing. Although significant action has been taken by
government, industry, and the advocacy community, new
revelations make it clear that the problem has yet to be solved.
The recent findings on Cd in children’s jewelry and other
children’s products have again ignited passions and are
triggering new, narrowly focused federal and state legislative
proposals in the U.S. (61).
New efforts to solve this problem would benefit from a
better understanding of the root causes, a clear view of the
roles of government, manufacturers, and retailers, and an
awareness of the constructive role that the nonprofit sector
can play. Effective regulation is an essential precondition,
necessary to establish an acceptable baseline level of safety
for product manufacturers, as well as for the government
agencies that are responsible for enforcing safety standards.
The road ahead will certainly be challenging. However, until
significant changes in policy and practice occur, consumers
cannot be confident that products they purchase for children
are safe, healthy, and environmentally sustainable.
Monica Becker has been an independent consultant for the past 2
years, working with government, industry, and academic organiza-
tions. Consulting contracts during this time were with: the Green
Chemistry and Commerce Council based at the University of Mas-
sachusetts Lowell; Green Depot (an on-line retailer of green products);
Harris Corporation; United Nations Environment Programme; the
New York Industrial Retention Network and the Rochester Institute
of Technology. Prior to that Ms. Becker held management positions
at the Rochester Institute of Technology, Golisano Institute for
Sustainability for 10 years. Sally Edwards is a Research Associate at
the Lowell Center for Sustainable Production at the University of
Massachusetts Lowell. Her work is currently funded by the New York
Community Trust and the Merck Family Fund. She is also serving as
an advisor to EcoLogo, an environmental certification organization
that is developing an eco-label for toys. She receives an honorarium
for this work from TerraChoice, the company that administers the
EcoLogo program. In her work to promote the development of
sustainable children’s products, Dr. Edwards interacts with many
manufacturers and retailers. In 2009, as a contractor to the Blu Skye
sustainability consulting firm she prepared slide presentations on toy
sustainability issues and design priorities for Walmart toy merchan-
disers to present to their major toy suppliers in China.Rachel Massey
is Policy Analyst and Policy Program Manager at the Massachusetts
Toxics Use Reduction Institute at the University of Massachusetts
Lowell. The Institute’s work is funded by the Commonwealth of
Massachusetts under the Toxics Use Reduction Act. Ms. Massey has
also received project funding from the Swedish Chemicals Agency and
the United Nations Environment Programme. Please address cor-
respondence regarding this article to monica@monicabecker.com.
Acknowledgments
The authors thank Janet Hutchins for significant contribu-
tions to researching and drafting this article; Ken Geiser, Joel
Tickner, Yve Torrie, and Cathy Crumbley for detailed
comments; and Ann Blake for the photo.
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ES1009407
VOL. 44, NO. 21, 2010 / ENVIRONMENTAL SCIENCE & TECHNOLOGY 97991
... Infants are especially vulnerable to the adverse short-and long-term health consequences of exposure to such toxic metals due to their higher metabolic rate, greater surface area to weight ratio, and accelerated growth of organs and tissues compared to adults. The deleterious health effects of these toxic trace elements on infants are detailed in Table 1 [7]. ...
... Regulatory efforts to address toxic chemicals in toys have included the enactment of the Consumer Product Safety Improvement Act (CPSIA) in 2008. This legislation placed restrictions on the presence of As, Cd, Pb, and Hg in children's products, including teethers, at levels of 25 ppm (µg g −1 ), 75 ppm, 100 ppm, and 60 ppm, respectively, as outlined in Table 1 [7]. Industry responses have included the establishment of the Toy Safety Certification Program by the Toy Industry Association, aimed at ensuring compliance with safety standards, albeit without surpassing existing regulations. ...
... Heavy metals (As, Cd, and Pb) have the potential to increase the risk of cancer in humans [7]. Prolonged exposure to low levels of these toxic metals could lead to various types of cancers. ...
Article
Full-text available
Infants are particularly vulnerable to exposure to toxic trace elements due to their developmental stage and behaviors such as mouthing and chewing on toys. Chemical exposure to heavy metals in infants’ toys is a significant concern as it poses a threat to their health and well-being. Therefore, quality control measures are essential to prevent infants’ exposure to potentially harmful metals. This study aimed to assess the presence of arsenic (As), cadmium (Cd), lead (Pb), and mercury (Hg) in infants’ teethers and evaluate potential health risks associated with their use. Eighteen teethers were analyzed for heavy metal content using inductively coupled plasma mass spectrometry (ICPMS). Results showed varying concentrations of As, Cd, Pb, and Hg in the teethers, with none exceeding the safety limits for these heavy metals set by regulatory bodies such as ASTM F-963 and EN 71. Furthermore, calculated exposure levels, including Chronic Daily Intake (CDI) and Lifetime Average Daily Dose (LADD), as well as risk assessments covering Hazard Quotient (HQ), Hazard Index (HI), Margin of Exposure (MOE), and Incremental Lifetime Cancer Risk (ILCR), indicated that the overall health risks associated with teethers’ use were non-existent. These findings highlight the importance of stringent regulations and ongoing monitoring of heavy metal levels in infants’ products to ensure their safety.
... The frequent hand-to-mouth activities of young children create a pathway for ingesting such chemicals from toys. Due to their faster metabolic rates, immature organ systems, rapid growth rates of organs and tissues, and high surface area-to-weight ratios, children are more vulnerable to these contaminants than adults [15,16]. Lower IQ, hyperactivity, and behavioural and learning disorders have been linked to PBDE exposure in children [17][18][19]. ...
... There are three potential reasons for the presence of toxic compounds in toys: either a lack of regulation, existing regulations are being violated, or loopholes in current regulations are being exploited [15]. In this case, we suspect the latter two reasons are more likely. ...
... Most children's toys sold in the EU are manufactured in China, where prices are as low as one-fifth of toys made in Europe [72]. The increasing demand for low-cost toys creates pressure on toy manufacturers, which may compromise toy quality through the use of cheap and potentially hazardous materials for production [15]. As a result, manufacturers may struggle to ensure compliance with EU regulations and global standards. ...
Article
Full-text available
Background With the high influx of low-cost plastic toys on the market, there is growing concern about the safety of such toys. Some of these plastic toys contains hazardous chemicals like polybrominated diphenyl ethers (PBDEs) due to the use of recycled plastics in new toy manufacturing. Here, we investigated if toys marketed in Europe are compliant with EU directives to assess the safety of currently used children's toys and identify implications of PBDE content in toys. Results Eighty-four toys purchased from international toy retailers were screened for bromine using X-ray fluorescence (XRF), and 11 of those with bromine content higher than 500 µg/g were analyzed for ten PBDEs using GC–HRMS. PBDEs were detected in all 11 toys. Ʃ10PBDE concentrations ranged up to 23.5 mg/g (with a median concentration of 8.61 mg/g), with BDE-209 being the most abundant compound (4.40 mg/g). Eight samples exceeded the EU’s Low POP Content Limit (LPCL) of 500 µg/g for the Ʃ10PBDEs by 6–47 times and the Unintentional Trace Contaminant (UTC) limits of 10 µg/g for Deca-BDE by 12–800 times. Conclusions PBDEs were up to percent levels, suggesting direct recycling of flame retarded plastic, e.g., e-waste plastics, into toy components. This is a call for concern and requires intervention from all stakeholders involved in the toy market. Overall, the occurrence of non-compliant toys in the EU market, as indicated in this study is primarily attributed to gaps in regulations, inadequate legislation for recycled plastics, the rise of online sales, complexities in global and national supply chains, and economic challenges. Failure to address these issues will hinder the efforts of the plastics industry to transition into a circular economy. This suggests that more actions are needed to address gaps in cross-border enforcement, and stricter sanctions are required for toy manufacturers who fail to adhere to regulations and safety standards.
... D espite the joy toys bring to children, improper toy selection can pose significant hazards, such as toxic materials, skin allergic, and choking risks (Becker et al., 2010;Fenner et al., 2020;Neofotistos et al., 2017). Choking hazards are especially concerning, causing thousands of emergency visits and fatalities among children in the United States (Centers for Disease Control and Prevention, 2002). ...
Article
We examined the impact of warning label size and design style on consumer attention to toy choking hazard warnings across three front-of-package (FOP) designs, using eye-tracking metrics. Our findings indicate that larger labels and high-contrast designs significantly enhance consumer attention. Additionally, typical warning placements on the FOP resulted in lower eye-tracking metrics. These results underscore the importance of safety compliance, as regulated label sizes and design styles enhance warning effectiveness. Revisiting warning label placement is also essential to improve hazard communication. These insights should guide toy manufacturers and importers in enhancing child safety by ensuring clearer, more effective warning labels.
... The presence of these complex organic compounds in flavors raises the potential safety concerns. In particular, many pharmaceutical excipients and food additives exhibited greater toxicity in children than in adults due to children's immature organ systems and developing barriers (Becker et al., 2010). It has been reported that glycerin, which is considered to be relatively nontoxic in adults, presents the neurotoxic effects in children (Peiré, 2019), and meanwhile, the accumulation of sorbitol could contribute to diabetic complications and even pose a risk of inducing liver damage (Rowe et al., 2009;Yochana et al., 2012). ...
Article
Full-text available
Flavors are widely utilized in the food and oral pharmaceutical industry, particularly in products for children, to enhance palatability and promote ingestion willingness. The complex compositions of flavors potentially induce severer toxicity especially in children. In this study, zebrafish embryos are applied for toxicity screening of flavor and its compounds by immersing in flavor solutions followed by the assessment of morphology of zebrafish larvae. Geraniol is identified as the prominent toxic compound and is considered highly toxic to zebrafish embryo. In further toxicology study, geraniol demonstrates the concentration‐dependent developmental toxicity as the obvious reduction of body and eye lengths, as well as the increased prevalence of tail deformities, pericardial edema, and spine deformation. Zebrafish larvae treated with geraniol exhibit reduction in liver area and exocrine pancreas length, increase in yolk sac area, as well as elevation of triglycerides and total cholesterol, which indicate the inhibited nutrient utilization. Transcriptome analysis reveals that under geraniol treatment, 248 differentially expressed genes (DEGs) are downregulated, whereas 23 DEGs are upregulated, and 110 DEGs are related to metabolic process. Biological processes of lipid metabolism, carbohydrate metabolism, protein hydrolysis, and transmembrane transport, including their involved functional genes, are all downregulated. These findings reveal the developmental toxicity of geraniol by affecting the nutrient utilization‐related organs development and biological processes. This study establishes an efficient screening model for identifying toxic flavor compounds during developing stages, thereby elucidating the potential safety risks of geraniol exposure in zebrafish and providing a comprehensive understanding of its potential toxicity mechanism.
Article
The leaching of metals from consumer products, especially those intended for children, poses significant health risks, particularly during prolonged exposure. This study investigates the release of metals from kindergarten books under conditions mimicking saliva, simulating real-world interactions where children may explore books orally. The experiment, conducted in a controlled lab, exposed books to a saliva-like solution for various time periods. Inductively Coupled Plasma Optical Emission Spectroscopy (ICP-OES) was used to quantify toxic metal concentrations (As, Cd, Cu, Ni, Pb). Results showed concentrations of toxic metals (mg/kg) ranging from 2.85 to 40.7 for As, 1.83 to 38.9 for Cd, 9.78 to 159 for Cu, 2.85 to 11.2 for Ni, and 36.1 to 111 for Pb. Correlation analysis revealed a significant positive correlation between As and Ni. Saline extraction produced no detectable As in some samples, while Cu was found in all. Stomach acid extraction showed varying levels of Pb, As, and Cu, indicating potential health risks. The health index (HI) for most samples exceeded 0.1 for As, Cu, and Pb, with As having the highest HI values. These findings highlight the risks of metal migration from printed materials and the need for safer alternatives in children's educational resources.
Article
Background: Children's vulnerability to chemical toxicant exposures demands strong consideration of the chemical composition of products designed for and marketed toward them. Inadequacies in health-protective legislation and lack of mandatory ingredient disclosure in most children's products have created significant gaps in protection and oversight. Scientific literature can provide insight into the chemical constituency of children's products that may be useful for prioritizing future regulatory efforts. Objective: We aimed to present a proof of concept for applying systematic evidence mapping methodology to identify which chemicals of potential concern have been reported in the scientific literature to be present in products marketed toward children, to inform future research and regulatory efforts. Methods: We conducted a broad, all-encompassing survey of the available literature from four databases to identify chemicals present in children's products. Using systematic evidence mapping methodologies, we constructed a database of children's products and their chemical constituents (termed "product-chemical combinations") based on a broad survey of current and relevant environmental health literature. Our study focused on chemicals present on the California Safer Consumer Products Program's Candidate Chemicals List, which includes chemicals with one or more known hazard traits. We then conducted an exploratory data analysis of product category and product-chemical combination frequencies to identify common chemicals in specific products. Results: Our systematic evidence mapping identified 206 potentially hazardous chemicals in children's products, 170 of which were found in toys. In total, we found 1528 distinct product-chemical combinations; 582 product-chemical combinations included chemicals known to be hazardous or potentially hazardous. Ortho-phthalates in plastic toys, parabens in children's creams/lotions, and bisphenols in both baby bottles and teethers were the most frequently encountered product-chemical combinations of potential concern. Discussion: The frequently reported presence of endocrine-disrupting chemicals in multiple types of children's products raises concerns for aggregate exposures and reveals gaps in regulatory protections for this sensitive subpopulation. Our reproducible and systematic evidence-based approach serves as a case study that can guide other prioritization efforts for transparent regulatory action aimed at improving the safety of chemicals in consumer products. https://doi.org/10.1289/EHP15394.
Article
Full-text available
The potential risk that heavy metals cause during the early stages of childhood development makes it a global health concern. The main aim of this study is to determine the concentration of cadmium, chromium, nickel-copper, and chromium (VI) to carry out the dose-response assessment, evaluating questionnaire responses given by children's parents in Lahore, Pakistan and calculate hazard quotient (HQ) to evaluate whether concentrations are above or below permissible limit. The concentrations detected by AAS in digested samples ranged from 83.7 mg/kg to-0.087 mg/kg for Cd, 806 mg/kg to-0.05 mg/kg for Cr (VI), 1001 mg/kg to-0.008 mg/kg for Pb, 822 mg/kg to-0.07 mg/kg for Cu, and 3000 mg/kg to-0.9 mg/kg for Ni. 40% samples for Cd, 5% samples for Cr (VI), 55% samples for Pb, and 5% samples for Ni exceeded the EU limit. Based on the HQ values detected, the trend of concentration of heavy metals exceeding EU regulations was Pb > Cd > Cr (VI) > Ni. Copper did not exceed any regulation yet present in many samples. Based on data from questionnaire responses and dose-response assessment using hazard quotient, heavy metal poisoning has been confirmed as a significant hazard because there are several health problems linked with it. Once heavy metals get into the living organisms, and the organism is exposed many times heavy metals are bioaccumulated. Hence, it can be harmful to mental health and the functioning of the central nervous system.
Chapter
Public alarm about the spate of recent product recalls throughout 2007, particularly of toys and other products used by children, has focused attention on the Consumer Product Safety Commission (the CPSC or the Commission). This scrutiny led to consideration of major amendments to the Consumer Product Safety Act (CPSA), which established and authorized the CPSC in 1972 in response to growing concerns about protecting the public from unsafe, defective consumer products. Jurisdiction over the administration and enforcement of several existing consumer safety statutes was transferred from other agencies to and consolidated under the CPSC. However, in the years since its establishment, the staff and resources of the CPSC have been considerably reduced, leading many observers to doubt its ability to fulfill its mission effectively. Consequently, Congress considered major reform legislation to address organizational and systemic deficiencies. Legislative proposals in the 110th Congress included provisions targeting specific consumer product defects and hazards. On July 29, 2008, H.Rept. 110-787, the Conference Report for H.R. 4040, the Consumer Product Safety Improvement Act of 2008 (CPSIA), was released after several months of negotiations in the conference committee to reconcile differences between the House and Senate versions of the bill. The bill passed the House of Representatives and the Senate on July 30, 2008 (424- 1) and July 31, 2008 (89-3), respectively. On August 14, 2008, President Bush signed the bill into law as P.L. 110-314. CPSC Chairman Nord and Commissioner Moore each expressed approval of the final legislation, with Chairman Nord expressing a desire for Congress to appropriate further funding to carry out the new mandates of the legislation. This report provides an overview of the prior authority of the CPSC to establish consumer product safety standards and to inspect and recall unsafe consumer products, and discusses P.L. 110-314, the Consumer Product Safety Improvement Act of 2008, reforming the CPSC and strengthening enforcement of consumer product safety standards.
Article
SHANGHAI, Sept. 7 — When Mattel, the world's largest toy maker, announced its third recall in six weeks this month, the company asked consumers to return toys because they contained dangerously high levels of lead paint. Toxic paint also turned up in several other products Mattel recalled in recent weeks, and in about 16 other recalls this year, including the popular Thomas & Friends train sets, according to the United States Consumer Product Safety Commission. All the products were made in China. Why is lead paint — or lead, for that matter — turning up in so many recalls involving Chinese-made goods? The simplest answer, experts and toy companies in China say, is price. Paint with higher levels of lead often sells for a third of the cost of paint with low levels. So Chinese factory owners, trying to eke out profits in an intensely competitive and poorly regulated market, sometimes cut corners and use the cheaper leaded paint. On the books, China's paint standards are stricter than those in the United States, requiring that paint intended for household or consumer-product use contain no more than 90 parts of lead per million. By comparison, American regulations allow up to 600 parts per million. The regulations are supposed to safeguard health, particularly in cases involving children, where ingesting excessive amounts of lead has been linked to disorders including mental retardation and behavioral problems.
Article
Congress enacted TSCA in 1976 to control risks from chemicals in commerce. It requires the government to review most new chemicals while they are being devel-oped and it gives government the power to regulate chemicals already in or entering commerce if they create an "unreasonable risk" to health or to the environment. Yet current policy hinders government's ability to gener-ate information and to act on such information when it indicates significant risk. This Article identifies 10 ele-ments that can facilitate a shift toward knowledge-driven policies that motivate and reward, rather than impede and penalize, the development of information sufficient to provide a reasonable assurance of chemical safety. Adopting a more comprehensive approach that seeks to develop good information on most or all chemicals would allow us to select safer chemicals with confidence. F or the last several decades, government policy has granted the tens of thousands of industrial chemicals already in commerce a strong "presumption of inno-cence. " In the absence of clear evidence of harm, companies have largely been free to produce and use such chemicals as they've seen fit. This policy contrasts sharply with the "pre-sumed guilty until proven innocent" approach adopted for pharmaceuticals and pesticides. For these substances, produc-ers have the burden of providing to the government informa-tion demonstrating their safety, at least when used as intended. Yet for industrial chemicals, the opposite is true: Gov-ernment—and, hence, the public—shoulders the burden of proof. In what amounts to a classic Catch-22, government must already have information sufficient to document potential risk, or at the very least, extensive exposure, in order to require the development of information sufficient to determine whether there is actual risk. This burden is so high that in the 32 years since the Toxic Substances Control Act (TSCA) 1 was enacted, the U.S. Environmental Protection Agency (EPA) has required testing for only about 200 chemicals. 2 Current policy essentially says: "We'll consider develop-ing a better understanding only of those chemicals that we already have good reason to believe pose a risk. " This is rather like the old adage about looking for lost car keys at night only under the streetlight because the light is better there. So when it comes to choosing among several available options to pro-vide a desired chemical function, or to replacing a problematic chemical, we are often in the dark and run the risk of simply "replacing the devil we know with the devil we don't. " Society remains largely ignorant about the risks of the great majority of chemicals because we only investigate those about which we already know something. That means we fail to learn not only which chemicals pose risks, but also which chemicals pose little or no risk. Adopting a more comprehensive approach that seeks to develop good information on most or all chemicals would allow us to select safer chemicals with confidence. TSCA places an even higher—some would say impossibly high—burden on EPA before it can act to control a chemi-cal. Government must effectively prove beyond all reasonable doubt that a chemical poses a risk in order to take any regula-tory action to restrict its production or use. Since adoption of 1. 15 U.S.C. 2601-2692, ELR StAt. TSCA 2-412. 2. Since 1979, EPA has used its test rule authority under TSCA 4, 15 U.S.C. 2603, to require testing of about 200 chemicals. For about 60 of these chemi-cals, the data were obtained through 4 Enforceable Consent Agreements (ECAs), which EPA uses as an alternative to test rules in cases where there is agreement with industry on the need and scope of testing. oFFiCE oF pollu-tion prEvEntion & toxiCS (oppt), u.S. EpA, ovErviEW: oFFiCE oF pollution prEvEntion And toxiCS progrAmS 4, 15 (2007), available at http://www.epa.gov/ oppt/pubs/oppt101c2.pdf [hereinafter OPPT ovErviEW, 2007].
Article
In 2006 the Massachusetts Toxics Use Reduction Institute conducted a study to determine if states could identify safer alternatives to five chemicals of concern. The chemicals investigated included di (2-ethylhexyl) phthalate (DEHP), formaldehyde, hexavalent chromium, lead and perchloroethylene. First, the Institute developed a methodology for assessing alternatives to these five chemicals that allowed it to quickly determine priority uses and alternatives to assess and to research the pertinent decision criteria, which included performance, technical, financial environmental and human health parameters. The methodology included important feedback from stakeholders in the state, which helped to focus and enhance the value of the work. Second, the Institute implemented the methodology over a ten month period. Based on the activities conducted by the Institute, safer alternatives were identified for each of the priority uses associated with the five chemicals studied. This report summarizes the methodology employed and provides examples of the results for one of the five chemicals, namely DEHP. The experience of the Institute and the information contained in this report indicates that alternatives assessment was a useful approach to organizing and evaluating information about chemicals and alternatives.
Article
Brominated flame retardants (BFRs), including polybrominated diphenyl ethers (PBDEs), 1,2-bis(2,4,6-tribromophenoxy)ethane (BTBPE), decabromodiphenyl ethane (DBDPE), and polybrominated biphenyls (PBBs) were found in children’s toys purchased from South China. The median BFR concentrations in the hard plastic toys were 53 000, 5540 ng/g, 101.1 ng/g, and 27.9 ng/g, for total PBDEs, DBDPE, BTBPE, and PBBs, respectively, which were notably higher than values in other toys. The PBDE concentrations were below the threshold limit (1000 ppm) required by the European Commission’s Restriction of Hazardous Substances (RoHS) and Waste Electrical and Electronic Equipment (WEEE) directives in all of the toys, except for one hard plastic toy with a total PBDE concentration of 5 344 000 ng/g. The BFR profiles in the toys were consistent with the patterns of their current production and consumption in China, where PBDEs, specifically decaBDE product, were the dominant BFR, followed by the emerging DBDPE. The relatively high concentrations of octa- and nonaBDEs in the foam toys and the results of principal component analysis (PCA) may suggest the decomposition of highly brominated BDEs during the manufacturing processes of the toys. Daily total PBDE exposures associated with toys via inhalation, mouthing, dermal contact, and oral ingestion ranged from 82.6 to 8992 pg/kg bw-day for children of 3 months to 14 years of age. Higher exposures, predominantly contributed through the mouthing pathway, were observed for infants and toddlers than for the other subgroups. In most cases, children’s BFR exposure via the toys likely accounts for a small proportion of their daily BFR exposure, and the hazard quotients for noncancer risk evaluation were far below 1. To the author’s knowledge, this is the first study to examine the concentrations of BFRs in toys, and the potential exposures to children.
Article
California's Proposition 65 now has been in effect for nearly twenty years, and it remains highly controversial. Media attention in recent years increasingly has focused on the statute's perceived excesses and some of its more sensational enforcement actions. The less frequently told story, however, is one of continued success in removing toxic chemicals from consumer products and industrial activities. This article discusses some of the more significant product reformulations triggered by enforcement of Proposition 65's warning requirement over the past five years, including reductions in lead in a wide variety of consumer products, and reduced exposures from toxins in children's playground equipment and portable classrooms. The article also describes enforcement actions that have led to warnings in grocery stores and restaurants about the dangers of mercury in fish for pregnant women and children. In many of these instances, Proposition 65 has filled gaps left by sluggish federal activity.
Article
Humans are exposed daily to a great number of xenobiotics and their metabolites present as pollutants. Bisphenol-A (BPA) is extensively used in a broad range of products including baby bottles, food-storage containers, medical equipment, and consumer electronics. Thus, BPA is the most common monomer for polycarbonates intended for food contact. Levels of this industrial product are found in maternal blood, amniotic fluid, follicular fluid, placental tissue, umbilical cord blood, and maternal urine. In this study, we investigated toxic effects of BPA concentrations close to levels found in serum of pregnant women on human cytotrophoblasts (CTB). These cells were isolated from fresh placentas and exposed to BPA for 24 h. Our results showed that very low doses of BPA induce apoptosis (2 to 3 times) as assessed using M30 antibody immunofluorescent detection, and necrosis (1.3 to 1.7 times) as assessed through the cytosolic Adenylate Kinase (AK) activity after cell membrane damage. We also showed that BPA increased significantly the tumor-necrosis factor alpha (TNF-α) gene expression and protein excretion as measured by real-time RT-PCR and ELISA luminescent test, respectively. Moreover, we observed that induction of AK activation and TNF-α gene expression require lower levels of BPA than apoptosis or TNF-α protein excretion. Our findings suggest that exposure of placental cells to low doses of BPA may cause detrimental effects, leading in vivo to adverse pregnancy outcomes such as preeclampsia, intrauterine growth restriction, prematurity and pregnancy loss.
Article
Foetal exposure to antiandrogens alters androgen-sensitive development in male rodents, resulting in less male-typical behaviour. Foetal phthalate exposure is also associated with male reproductive development in humans, but neurodevelopmental outcomes have seldom been examined in relation to phthalate exposure. To assess play behaviour in relation to phthalate metabolite concentration in prenatal urine samples, we recontacted participants in the Study for Future Families whose phthalate metabolites had been measured in mid-pregnancy urine samples. Mothers completed a questionnaire including the Pre-School Activities Inventory, a validated instrument used to assess sexually dimorphic play behaviour. We examined play behaviour scores (masculine, feminine and composite) in relationship to (log(10)) phthalate metabolite concentrations in mother's urine separately for boys (N = 74) and girls (N = 71). Covariates (child's age, mother's age and education and parental attitude towards atypical play choices) were controlled using multivariate regression models. Concentrations of dibutyl phthalate metabolites, mono-n-butyl phthalate (MnBP) and mono-isobutyl phthalate (MiBP) and their sum, were associated with a decreased (less masculine) composite score in boys (regression coefficients -4.53,-3.61 and -4.20, p = 0.01, 0.07 and 0.04 for MnBP, MiBP and their sum respectively). Concentrations of two urinary metabolites of di(2-ethylhexyl) phthalate (DEHP), mono-(2-ethyl-5-oxohexyl) phthalate (MEOHP) and mono-(2-ethyl-5-hydroxyhexyl) phthalate (MEHHP) and the sum of these DEHP metabolites plus mono(2-ethylhexyl) phthalate were associated with a decreased masculine score (regression coefficients -3.29,-2.94 and -3.18, p = 0.02, 0.04 and 0.04) for MEHHP, MEOHP and the sum respectively. No strong associations were seen between behaviour and urinary concentrations of any other phthalate metabolites in boys, or between girls' scores and any metabolites. These data, although based on a small sample, suggest that prenatal exposure to antiandrogenic phthalates may be associated with less male-typical play behaviour in boys. Our findings suggest that these ubiquitous environmental chemicals have the potential to alter androgen-responsive brain development in humans.