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. 2023 Mar 13;131(3):031304. doi: 10.1289/EHP12630

Invited Perspective: Examining Chemicals in Food as a Priority for Toxicity Testing

Courtney C Carignan 1,
PMCID: PMC10010385  PMID: 36913235

In their new paper,1 Zhao et al. present an elegant computational approach to estimate concentrations of exogenous chemicals in human blood and calculated corresponding toxic equivalencies to prioritize toxicity testing. Application of their new model identified a surprisingly high proportion of food additives, indirect additives, and food-contact substances predicted to have the highest total toxic equivalencies [referred to by Zhao et al. as bioanalytical equivalencies (BEQ%)] for the general population. Other predominant categories included industrial chemicals, pesticides, and household, fragrance, and personal care products.

Zhao et al. used biomonitoring2 and ExpoCast3 data for 216 compounds to train and test a machine learning algorithm. They employed the model to predict blood concentrations for 7,858 chemicals from ToxCast,4 which they used to calculate %BEQ for 12 endocrine-disruption assays. The authors listed the top 25 chemicals with the highest BEQ% for each of the assays, a total of 145 unique chemicals, in their Excel Table S8. I visualized these results in Figure 1 by summing BEQ% by application category and within each category by assay end point.

Figure 1.

Figure 1 is a pie chart displays the following information: Pesticides are 9 percent, Food additives, indirect additives and contact substances are 38 percent, household fragrance and personal care are 21 percent, and industrial uses are 31 percent. The following information is given: Pesticides: Metabolic are 32 percent, thyroid hormone are 31 percent, estrogen are 25 percent, androgen are 12 percent. Food additives, indirect additives and contact substances: Metabolic are 51 percent, Androgen are 31 percent, Thyroid hormone are 13 percent, and Estrogen are 5 percent. Household fragrance and personal care: Estrogen are 33 percent, Androgen are 25 percent, Thyroid hormone are 28 percent, and Metabolic are 14 percent. Industrial uses: Androgen are 45 percent, Metabolic are 36 percent, Estrogen are 16 percent, and Thyroid hormone are 3 percent.

Proportional summed toxic equivalencies by application category and within each category by ToxCast end point (n=145). Application categories derived by summing bioanalytic equivalencies (BEQ%1+ BEQ%2) for chemicals within each category in Zhao et al., Excel Table S8.1

The unexpected predominance of the 50 food additives, indirect additives, and food-contact substances identified by this research highlights the need for comprehensive and agnostic approaches to toxicity testing prioritization. Resulting BEQ% were especially notable for two flavoring agents (2,3-butanedione and methyl formate), a colorant (FD&C Yellow 5), and three plasticizers used in food-contact substances (dimethyl isophthalate, diisobutyl phthalate, and diethyl phthalate), indicating the need to prioritize these chemicals for closer evaluation. Rigorous evaluation is also a priority among consumers, who are increasingly choosing organic foods and those with fewer ingredients and less packaging in an effort to avoid potentially harmful chemical exposures.5

Chemical production is on the rise,6 and only a small fraction of the estimated 350,000-plus chemicals in commerce have undergone careful screening or testing.7 Identification of harmful chemicals in commerce with widespread exposure has been ongoing for decades.8 Notorious examples include dichlorodiphenyltrichloroethane (DDT), lead, radium, dioxins, polybrominated diphenyl ethers, phthalates, bisphenols, and per- and polyfluoroalkyl substances.9,10 These discoveries have occurred alongside soaring rates of chronic diseases and conditions—including infertility, metabolic syndrome, thyroid disease, cancer, and neurodevelopmental and neurodegenerative conditions—that are not fully accounted for by genetic, lifestyle, or nutritional factors11 and that have been linked with exposure to many of these contaminants.12

The new model can also be used to screen alternatives that may have been introduced without adequate toxicity testing, potentially avoiding the continued use of regrettable substitutions. For example, one of the plasticizers identified by Zhao et al. for prioritization, diisobutyl phthalate, has been used as a replacement for di(2-ethylhexyl) phthalate.13 The authors also identified tri-isobutyl phosphate for prioritization; this compound is in the class of organophosphate flame retardants that have been widely used as replacements for polybrominated diphenyl ethers.14,15

Zhao et al. trained the model using biomonitoring data from the nationally representative National Health and Nutrition Examination Survey (NHANES),2 so it should be reasonably inclusive of communities with disparate burdens of chemical exposures. Improved chemical prioritization for toxicity testing is vital to better protect low-income communities and communities of color. A future evaluation of model performance could test the accuracy of predictions among vulnerable and sensitive populations. The authors noted several other ways to improve the model, such as use of more robust toxicity data and periodic future updates to incorporate new estimates of exposure and measured blood concentrations of chemicals.1

The task of predicting population blood concentrations for thousands of chemicals is seemingly impossible, yet it is a necessary step in overhauling current methods for prioritization of chemicals for toxicity testing. I applaud Zhao et al. for their innovative approach to tackling it.

Acknowledgments

C.C.C. is supported in part by the National Institute of Environmental Health Sciences, National Institutes of Health (R01ES028311), the U.S. Environmental Protection Agency National Priorities Program (No. 84025201 and Assistance Agreement No. R839482), and the U.S. Department of Agriculture National Institute of Food and Agriculture (Hatch Project MICL02565). This perspective has not been formally reviewed by the funding agencies. The views expressed in this document are solely from the author and do not necessarily reflect those of the funding agencies. The agencies do not endorse any products or commercial services mentioned in this paper.

Refers to https://doi.org.10.1289/EHP11305

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