Robust data from longitudinal birth cohort studies and experimental studies of perinatally exposed animals indicate that exposure to ortho-phthalates can impair brain development and increase risks for learning, attention, and behavioral disorders in childhood. This growing body of evidence, along with known adverse effects on male reproductive tract development, calls for immediate action.

Exposures are ubiquitous; the majority of people are exposed to multiple ortho-phthalates simultaneously. We thus recommend that a class approach be used in assessing health impacts as has been done with other chemical classes. We propose critically needed policy reforms to eliminate ortho-phthalates from products that lead to exposure of pregnant women, women of reproductive age, infants, and children. Specific attention should be focused on reducing exposures among socially vulnerable populations such as communities of color, who frequently experience higher exposures.

Ortho-phthalates are used in a vast array of products and elimination will thus necessitate a multipronged regulatory approach at federal and state levels. The fact that manufacturers and retailers have already voluntarily removed ortho-phthalates from a wide range of products indicates that this goal is feasible.

As experts in toxic chemicals and neurodevelopment who are members of Project TENDR (Targeting Environmental Neuro-Development Risks), we have determined that exposure to ortho-phthalates can impair child brain development and increase children’s risks for learning, attention, and behavioral disorders. There are robust data from longitudinal birth cohort studies conducted over the last decade that have shown associations between prenatal exposures to ortho-phthalates and attention-deficit hyperactivity disorder (ADHD), other behavioral problems, adverse cognitive development including lower IQ, poorer psychomotor development, and impaired social communication.

This growing body of evidence, along with the known adverse effects on male reproductive tract development of ortho-phthalates, calls for immediate action. Given that general population exposure is ubiquitous and is to a mixture of multiple ortho-phthalates simultaneously, we recommend that assessment of hazard use a class approach, as has been done for a number of other chemical classes. To protect child brain development, ortho-phthalates need to be removed from consumer products that contribute to exposure of pregnant women, women of reproductive age, infants, and children. We summarize the epidemiological evidence on adverse neurodevelopmental effects following prenatal exposure to ortho-phthalates, discuss sources of exposure and what is known about potential mechanisms, and propose urgently needed reforms to substantially reduce exposures to ortho-phthalates over critical periods of child brain development.

Ortho-phthalates are diesters of phthalic acid and are the predominate type of phthalate used in commerce. (For simplicity, we will refer to them as phthalates.) They are high-production-volume chemicals used most often as a plasticizer in polyvinyl chloride (PVC) and other plastics. Phthalates are used in numerous consumer products, including food production materials and packaging; medical supplies and coatings of medicines; flooring, wall coverings, and other home materials; and cosmetics and other personal care products.1 Approximately 4.9 million metric tons are produced annually worldwide (reviewed in Ejaredar et al.2). The highest-production phthalates are di-2-ethylhexyl phthalate (DEHP), diisononyl phthalate (DiNP), butylbenzyl phthalate (BBzP), dibutyl phthalates (DBPs), and diethyl phthalate (DEP).3

Diet is a particularly important exposure pathway for some phthalates, including DEHP and DiNP.4 Phthalates have been shown to leach into food from plastic equipment like tubing used in commercial dairy operations, lid gaskets, food preparation gloves, conveyor belts, and food packaging materials.5 As such, consumption of fast food and other dining-out sources,5 as well as lipophilic foods such as dairy,4 can be important dietary sources of phthalate exposures.

Building products containing phthalates, such as vinyl flooring and wall coverings, have a large surface area from which phthalates can migrate into the indoor air and household dust, also resulting in human exposure.6 Historically, phthalates were added to children’s toys, although use of multiple phthalates in toys has been banned by the Consumer Product Safety Commission (CPSC; see the box on page 689).1,7

I. Federal Regulatory Action
A. US Environmental Protection Agency (EPA)
• Set a drinking water standard for DEHP (6 ppb).8
• Listed DEHP and DBP as hazardous air pollutants and as substances on the Toxic Release Inventory that must be reported to EPA if released into any media.8
• Listed phthalates as hazardous waste if discarded as commercial chemical products under the Resource Conservation and Recovery Act.8
• Recently designated 5 phthalates (DnBP, DiBP, BBzP, DEHP, and DCHP) as high-priority substances for risk evaluation under the Toxic Substances Control Act.9
B. US Consumer Product Safety Commission
• Banned 8 ortho-phthalates from use in children’s toys and childcare articles: DEHP, DBP, BBzP, DINP, DiBP, DPENP, DHEXP, and DCHP.10 The regulation is under legal challenge by the National Association of Manufacturers, the American Chemistry Council, and other industry groups.11
C. US Food and Drug Administration (FDA)
• Set maximum concentration of DEHP in bottled water at the same concentration that EPA had set in drinking water.12
• Issued guidelines (but not regulation) recommending that DBP and DEHP be avoided as excipients in prescription and nonprescription products,13 advised manufacturers to label medical devices that contain DEHP,14 and concluded that exposure to DEHP received by some infants from medical device–related sources could be substantially greater than the agency’s estimate of the Tolerable Intake.15
• Approved use of 28 phthalates as food additives in food contact articles.16,17 Uses include as plasticizers, binders, coating agents, defoamers, and gasket closures, in materials such as cellophane, paper and paperboard, and plastics.
• Has failed to meet the statutory deadline for final decisions on 3 recently submitted petitions that could substantially reduce dietary exposure to phthalates.17 o Two were submitted by 11 environmental and public health organizations and requested that FDA strike from its existing regulations its approvals of all 28 phthalates as food additives in food contact articles, as the agency could no longer conclude that such use is safe, as is required by law.17
o The third petition was submitted by the Flexible Vinyl Alliance and requested that FDA revoke its approval of 24 phthalates that the Alliance claims are no longer used as food additives in food contact applications.17 The industry petition did not include several approved uses of these phthalates and continued the approval of DEHP, DINP, DCHP, and DIDP as food additives.
II. Examples of Voluntary Action by Retailers and Manufacturers
• Home Depot’s safer chemicals policy includes restrictions on phthalates as a class in vinyl flooring and wall-to-wall carpet.18,19
• Lowe’s, Lumber Liquidators, and Menards have taken action to remove phthalates as a class from vinyl flooring.19,20
• Apple has removed phthalates as a class from almost all products.21
• Hewlett Packard has removed multiple phthalates from commercial personal computer products and a lesser number from other products.22
• IKEA has removed phthalates from a number of its products.23
• Mohawk,24 Tarkett,24 SC Johnson,25 and Steelcase26 have restricted use of phthalates in some products, including household products.
• Ahold Delhaize, the fourth largest grocery chain in the United States (with 2000 stores including Food Lion, Giant Food, Giant/Martin’s, Hannaford, and Stop & Shop) recently announced restrictions on phthalates and other chemicals in its own branded products in the following categories: all grocery, baby food and infant formula, and formulated laundry products, as well as personal care, cosmetic, and baby products.27,28
• CVS Health,29 Loblaw,29 Rite Aid,30 and Walmart31 are also reducing the use of phthalates in beauty and personal care products and household products with the goal of elimination.
• Sephora set a goal to reduce high-priority chemicals including 8 phthalates by 50% over the next 3 years.32,33
• Panera Bread has replaced vinyl gloves, which must be softened with phthalates or other plasticizers, with safer alternatives such as polyethylene gloves that require no such chemical additives.33
III. Examples of Health Care Organization and Medical Supplier Actions
• Dignity Health,34 Hackensack Meridian Health,35 and Kaiser Permanente36 have a stated preference for products made without phthalates.
• Warner Chilcott recently brought a new product to market, Delzicol (mesalamine), which does not contain DBP in the medication coating.37
In totality, these examples demonstrate the feasibility of reformulating a vast array of products to remove phthalates. Cited references can help inform steps necessary in selection of safer alternatives when replacing phthalates.38–40

Note. BBzP = butylbenzyl phthalate; DBP = dibutyl phthalate; DCHP = dicyclohexl phthalate; DEHP = di-2-ethylhexyl phthalate; DHEXP = di-n-hexyl phthalate; DiBP = diisobutyl phthalate; DIDP = di-isodecyl phthalate; DINP = diisononyl phthalate; DnBP = di-n-butyl phthalate; DPENP = di-n-pentyl phthalate; and ppb = parts per billion.

Phthalates including DEP and DBPs are commonly used in cosmetics and other personal care products, and are sometimes used as excipients in medications and supplements (see the box on page 689).2 For example, DEP and DBPs are used in a wide range of personal care products including nail polish, lotions, fragrances, and hair-styling products.41 Numerous studies have found correlations between personal care product use and the concentrations of phthalate metabolites in urine.41 Overall, women have higher exposure to phthalates found in personal care products than men, and Black and Latina women have higher exposure to certain phthalates compared with White women, independent of socioeconomic status.42 Phthalates are readily transferred from mother to fetus during pregnancy.2

US population exposure to phthalates has changed in the last decade.7 Exposures to di-n-butyl phthalate (DnBP), BBzP, and DEHP have declined, while exposures to replacement phthalates such as DiNP and diisobutyl phthalate (DiBP) have increased. The observed temporal trends are likely a reflection of legislative activity and advocacy efforts of nongovernmental organizations, as well as changes by manufacturers and retailers in response to consumer preference (see the box on page 689).7

Historically, most of the health concerns and regulations pertaining to phthalates were motivated by strong toxicological evidence showing adverse antiandrogenic effects on male reproductive tract development.1 More recently, an increasing number of prospective epidemiological studies have found associations between prenatal exposure to phthalates and adverse neurodevelopment in offspring.43 A recent systematic review of the human data concluded that prenatal exposure to DEHP, DBPs, DEP, and BBzP has an adverse impact on cognitive and psychomotor development, internalizing and externalizing behaviors, attention, gender-related play behaviors, social responsiveness, and visual spatial abilities of children.43 As of 2019, there were more than 30 published studies that have measured prenatal exposure to phthalates using validated exposure biomarkers43–49 or environmental estimates of prenatal exposure50,51 in longitudinal cohorts assembled from 11 different countries or territories around the globe. Children have been followed for altered neonatal behavior or infant visual recognition memory, cognitive development, behavior, executive function, reciprocal social behavior, gender-related play behaviors, and for symptoms of, or clinical diagnosis with, developmental disabilities including autism and ADHD. Examples of key findings from this extensive literature base are discussed in the following paragraphs.

The most consistent pattern across multiple studies is associations with behaviors commonly associated with ADHD (including hyperactivity, aggression/defiance, and emotional reactivity),43 deficits in executive function,52,53 or ADHD clinical diagnosis.54 For example, a 2018 study nested within the Norwegian Mother and Child Cohort leveraged a linkage between this cohort and the Norwegian National Patient Registry, which collects all outpatient diagnoses from specialty clinics. Engel et al. measured second-trimester urinary phthalates and found that children of mothers that fell in the highest quintile of prenatal exposure to DEHP metabolites had almost 3 times the odds of being diagnosed with ADHD as those with mothers in the lowest quintile (odds ratio [OR] = 2.99; 95% confidence interval [CI] = 1.47, 5.49).54

Phthalates, particularly metabolites of DBP and DEHP, have also been associated with more problem behaviors, as estimated by validated inventory-based behavioral rating scales in these largely subclinical populations. For example, Lien et al. reported that third-trimester urinary concentrations of DnBP and DEHP metabolites were associated with more externalizing problems, more delinquent behaviors, and more aggressive behaviors, as measured by the Child Behavior Checklist, in a population of 8-year-old children in Taiwan.55 Also using the Child Behavior Checklist and leveraging a US-based multicenter pregnancy cohort enrolled in California, Minnesota, Missouri, and Iowa, Kobrosly et al. reported that third-trimester urinary DiBP metabolites were associated with more inattention, rule-breaking behavior, aggression, and conduct problems.56 DEHP and BBzP metabolites were also linked with altered behavior that was in some cases sex-specific. Another recent study found an association between prenatal exposure to the sum of low-molecular-weight phthalates (which includes metabolites of DBPs and DEP) and hyperactivity, attention problems, and anxiety at the age of 16 years.49

In addition, phthalates have been associated with altered child executive functions using both rater-based and performance-based assessments. Executive functions are higher-order cognitive processes that support goal-directed behaviors and are typically impaired in children with ADHD. Factor-Litvak et al. reported that prenatal DBP metabolites were associated with poorer working memory in a birth cohort enrolled in New York City and administered the Wechsler Intelligence Scale for Children-IV at age 7 years.53 Engel et al. reported that prenatal metabolites of DBP were associated with poorer working memory on the Behavior Rating Inventory of Executive Function.52 Factor-Litvak et al. also found that prenatal metabolites of DBPs were associated with a significant linear reduction in child IQ. Overall, child IQ was 7 points lower in the highest versus lowest quartile of DBP exposure. DBP metabolites were also associated with index-specific decrements in processing speed, perceptual reasoning, and verbal comprehension.53 Maternal urinary concentrations of BBzP metabolites were also associated with reductions in child perceptual reasoning.53

It is important to note that the literature is not entirely consistent, particularly among studies that focus on cognitive development during infancy and early childhood. Among these studies, there is often a lack of overlap in the specific metabolites implicated, the gender most affected, or the direction of the relationship. Even among studies of neurobehavior, not all have found associations,48,49,57,58 and some have found associations primarily with internalizing domains.59,60 Some of these differences may be attributable in part to differences in the study designs, including the age of the child at testing, the gestational age at urine sample collection, and the instruments used for assessing neurodevelopmental outcomes measures. In addition, early studies of phthalates and neurobehavior summed phthalate metabolites into low- and high-molecular-weight groupings, which makes it difficult to compare results to those reporting findings on individual phthalates, particularly in light of temporal changes of the contribution of specific phthalates to the overall exposure mixture.

Despite these differences, the weight of evidence strongly supports a relationship between certain phthalates and altered neurobehavioral development. This interpretation is additionally supported by the Chronic Hazard Advisory Panel for the CPSC, which concluded that poorer neurodevelopment test scores are generally associated with higher maternal prenatal urinary concentrations of metabolites of DEHP, DBPs, and DEP, and that human exposure to these phthalates should be reduced.1 Consistent with the systematic review by Zhang et al.,43 a 2015 review also concluded that prenatal exposures to DEP, BBzP, DEHP, and DBPs were associated with adverse cognitive and behavioral outcomes in children, including lower IQ and problems with attention, hyperactivity, and poorer social communication.2

Studies of gestational and early life exposure in animal models, which have mostly focused on DEHP, are generally consistent with the observations from epidemiological studies. The most consistently observed effects include hyperactivity, anxiety and depressive behaviors, and cognitive impairments including impacts on learning and memory.61 Disruption of the organization and function of the hypothalamic–pituitary–gonadal axis by phthalates known to inhibit fetal testosterone production is also frequently reported.61 A particularly compelling study showed that rats perinatally (both before and after birth) exposed to a human-relevant phthalate mixture displayed lower cognitive flexibility in a set-shifting task, an outcome that correlated with fewer synapses in the prefrontal cortex.62 Sensitive windows of exposure span pre- and postnatal life through adolescence63 including puberty64–66 and possibly adulthood,67–70 which is unsurprising given that complex structures including the prefrontal cortex, hippocampus, and cerebellum undergo significant development well into early adulthood.

Consistent with the epidemiological findings, animal outcomes are frequently sex-specific. It is known that many phthalates are antiandrogenic1 although antiestrogenic effects have also been reported in vitro.71 It has been hypothesized that the differential effect of phthalates on neurobehavioral outcome by sex seen in many studies may result from disrupted fetal testosterone production. Critically, unlike rodents in which testosterone is aromatized to estrogen in the developing brain and then acts via estrogen receptors to masculinize the male brain, in genetically male humans testosterone acts primarily via the androgen receptor.70 Thus, while the phenomenon of sex-specific effects may be conserved across species, specific effects within sex may vary based on taxonomical differences in steroid hormone function. Phthalates can also modulate aromatase activity in the developing brain, which can interfere with estrogen synthesis.72,73 This is of concern because estrogen plays a critical role in brain plasticity and other developmental refinements,74 and there is also growing evidence that estrogen synthesis can be extragonadal, including in the brain.75

The hippocampus and, consequently, aspects of neural plasticity, cognitive flexibility, anxiety-like behavior, learning, and memory, are thought to be particularly vulnerable to phthalates. For example, male mice prenatally exposed to DEHP had evidence of oxidative stress, neuronal loss, and neuroinflammation in the hippocampus as adults, along with elevated anxiety behavior and impaired recognition memory.76,77 Similarly, male rats perinatally exposed to DEHP had impaired dendritic complexity in the hippocampus, particularly in CA1 pyramidal neurons.78

A recent review of the phthalate literature discussed several additional potential mechanisms to explain the epidemiological and animal toxicity literature.3 Disruption of thyroid hormone pathways is one potential mechanism of interest, given that thyroid hormone is essential for brain development. There is also evidence of altered ion homeostasis including calcium signaling, peroxisome proliferator-activated receptors activation, and lipid metabolism, particularly in the hippocampus.

In summary, multiple longitudinal studies of human prenatal phthalate exposure have found evidence of altered neurobehavioral development. These findings are of concern especially in light of the supporting evidence from experimental studies and a growing understanding of the mechanisms whereby phthalates may adversely affect fetal brain development. Given the widespread exposures to phthalates, including among women and children, and the limited existing US regulations, none of which focus on pregnant women, health-protective regulatory actions are required to eliminate these potentially harmful exposures.

Mounting evidence on the impacts of phthalates on children’s brain development compels meaningful actions to eliminate exposure for women of reproductive age, pregnant women, infants, and children. As discussed, human exposure to phthalates ranges from foods to building materials to medical products, pharmaceuticals, cosmetics, and other personal care products. Therefore, reducing human exposure necessitates a multipronged approach through regulations at the federal and state levels, as well as through voluntary action on the part of retailers and manufacturers.

To date, federal regulation of phthalates in the United States has been minimal with several exceptions, including restrictions on 8 phthalates in children’s toys and childcare articles (see the box on page 689). We strongly urge both federal and state agencies to move rapidly to eliminate phthalate use. Specific attention should be focused on reducing exposures among socially vulnerable populations such as communities of color, who frequently experience higher exposures.42 States should not wait for the federal government to act, as state action can galvanize federal regulation. It is encouraging that voluntary action on the part of manufacturers, retailers, and health care organizations has removed phthalates from a wide range of products (see the box on page 689). Consumer pressure is critical to motivate additional manufacturers and retailers to act, as well as to encourage federal and state regulation.

We recommend that the evaluation of hazards of phthalates use a class approach as has been done for other classes of chemicals (e.g., organophosphate pesticides, dioxin-like compounds) and as has recently been recommended by a National Academy of Sciences report on organohalogen flame retardants.79,80 This approach is appropriate given that general population exposure is to mixtures of phthalates, coupled with the fact that phthalates have similarities in chemical structures, metabolism, and biological activity, including disruption of multiple endocrine systems, and have common health outcomes, including adverse effects on child neurodevelopment and male reproductive tract development, as well as other adverse effects.

Following are 5 critical recommendations for reducing phthalate exposures:

    to reduce dietary exposure,

    to reduce exposure from medical supplies and medication,

    to reduce exposure from personal care products and other household products,

    to reduce exposure from a broad range of other products including building materials, and

    to reduce risk of regrettable substitution.


The US Food and Drug Administration (FDA) must remove from its existing regulations its approvals of all 28 phthalates for use in food packaging and other materials that come in contact with food. There is no longer any basis for the agency to conclude that there is “reasonable certainty of no harm” from these uses, which is the legal standard for safety of food contact materials under the federal Food, Drug, and Cosmetic Act (see 21 CFR [updated September 19, 2019]), which governs FDA’s actions. All of the phthalates that have been associated with adverse child neurodevelopment, discussed previously, are currently approved by FDA for food contact use.

Until the FDA takes action to protect the food supply from phthalates, the food industry, including producers, processors, retailers, and restaurant chains, should investigate, identify, and remove sources of phthalates from their food products.

Medical Supplies and Medication

The use of phthalates in medications and medical devices also falls under FDA jurisdiction. While FDA has published guidelines to address many of these sources (see the box on page 689), the agency must promulgate regulations to eliminate their uses.

Personal Care and Other Household Products

Authority to regulate phthalates in cosmetics (which are defined broadly to include many personal care products) also falls under FDA jurisdiction. However, the agency’s authority is much less comprehensive and health protective than its authority to ensure the safety of food or drugs. This needs to be rectified by congressional action.

The CPSC has authority to ensure the safety of consumer products and is to be commended for eliminating a number of phthalates from children’s toys. However, the agency must also take action to prohibit the sale of other phthalate-containing products that fall under its jurisdiction.

In addition to federal action, elimination of phthalates from personal care and household products requires action on the part of states, manufacturers, and retailers.

Personal care and household products must be labeled if they contain phthalates so consumers can make informed decisions to avoid these substances if desired.

Building Materials and Other Products

The US Environmental Protection Agency (EPA) must use its authority under the Toxic Substances Control Act (TSCA; 15 USC Ch 53 [2016]) to regulate phthalates. EPA has recently embarked on a multiyear process for evaluating the risk of several phthalates under TSCA. The agency must broaden this effort using a class approach in assessing health impacts. Furthermore, EPA should aggressively exercise its authority to regulate the manufacture, import, processing, distribution in commerce, disposal, and known and reasonably foreseeable uses of phthalates.

Regrettable Substitution

Assessment to identify safer alternatives to phthalates must consider adverse effects to human health and the environment as well as societal impacts along with performance and costs.80 This is critical given the potential for regrettable substitution and the availability of lower-hazard alternatives (see the box on page 689 for resources on approaches for selecting safer alternatives). No phthalate should be used as a substitute for another phthalate, as has already been done with DiNP for DEHP. In addition, PVC plastics should be replaced with safer materials that do not require plasticizers. The substitution of safer alternatives for phthalates is critical given the risk these chemicals pose to child brain development.

Substantial evidence links exposure to phthalates with increased risks for child learning, attention, and behavioral problems. We therefore recommend that phthalates be eliminated from products that may lead to exposure of women of reproductive age, pregnant women, infants, and children. As discussed, this will necessitate a multipronged approach through regulations at the federal and state levels, as well as through voluntary action on the part of retailers and manufacturers. However, given that manufacturers have already successfully removed phthalates from a wide range of products, including food, medicine and medical supplies, personal care products, and other household and building materials (see the box on page 689), we believe the goal of phthalate elimination is achievable.

See also Birnbaum and Bornehag, p. 551.


We acknowledge that authors of this article have received funding from the following entities: The National Institute of Environmental Health Sciences: P30ES010126 (S. M. E.), R01ES021777 (S. M. E.), P30ES023513 (D. H. B.), P30ES025128 (H. P.), and R01ES009718 (R. H.); the John Merck Fund (C. B., M. S.); the Passport Foundation, Ceres Trust, and Pediatric Epilepsy Research Foundation (M. S.); the Clarence E. Heller Charitable Foundation (C. B.); the Marisla Foundation; and the Forsythia Foundation (A. Z.).


The authors report no conflicts of interest.


This is a review article and, thus, institutional board review was not required.


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Stephanie M. Engel, PhD, Heather B. Patisaul, PhD, Charlotte Brody, RN, Russ Hauser, MD, ScD, MPH, Ami R. Zota, ScD, MS, Deborah H. Bennet, PhD, Maureen Swanson, MPA, and Robin M. Whyatt, DrPHStephanie M. Engel is with the Department of Epidemiology, Gillings School of Global Public Health, University of North Carolina at Chapel Hill. Heather B. Patisaul is with the Department of Biological Sciences, Center for Human Health and the Environment, North Carolina State University, Raleigh. Charlotte Brody is with Healthy Babies Bright Futures, Charlottesville, VA. Russ Hauser is with the Department of Environmental Health at the Harvard T. H. Chan School of Public Health, Boston, MA. Ami R. Zota is with the Department of Environmental and Occupational Health, George Washington University Milken School of Public Health, Washington, DC. Deborah H. Bennet is with the Department of Public Health Sciences, School of Medicine, University of California at Davis. Maureen Swanson is with The Arc of the United States, Washington, DC. Robin M. Whyatt is with the Department of Environmental Health Sciences, Mailman School of Public Health, Columbia University, New York, NY. “Neurotoxicity of Ortho-Phthalates: Recommendations for Critical Policy Reforms to Protect Brain Development in Children”, American Journal of Public Health 111, no. 4 (April 1, 2021): pp. 687-695.

PMID: 33600256