Skip to main page content
U.S. flag

An official website of the United States government

Dot gov

The .gov means it’s official.
Federal government websites often end in .gov or .mil. Before sharing sensitive information, make sure you’re on a federal government site.

Https

The site is secure.
The https:// ensures that you are connecting to the official website and that any information you provide is encrypted and transmitted securely.

Access keys NCBI Homepage MyNCBI Homepage Main Content Main Navigation
. 2024 Sep;132(9):97001.
doi: 10.1289/EHP13937. Epub 2024 Sep 4.

Impact of Skin Care Products on Phthalates and Phthalate Replacements in Children: the ECHO-FGS

Affiliations

Impact of Skin Care Products on Phthalates and Phthalate Replacements in Children: the ECHO-FGS

Michael S Bloom et al. Environ Health Perspect. 2024 Sep.

Erratum in

Abstract

Background: Phthalates and their replacements have been implicated as developmental toxicants. Young children may be exposed to phthalates/replacements when using skin care products (SCPs).

Objectives: Our objective is to assess the associations between use of SCPs and children's urinary phthalate/replacement metabolite concentrations.

Methods: Children (4-8 years old) from the Environmental Influences on Child Health Outcomes-Fetal Growth Study (ECHO-FGS) cohort provided spot urine samples from 2017 to 2019, and mothers were queried about children's SCP use in the past 24 h (n=906). Concentrations of 16 urinary phthalate/replacement metabolites were determined by liquid chromatography-tandem mass spectrometry (n=630). We used linear regression to estimate the child's use of different SCPs as individual predictors of urinary phthalate/replacement metabolites, adjusted for urinary specific gravity, age, sex assigned at birth, body mass index, and self-reported race/ethnic identity, as well as maternal education, and season of specimen collection. We created self-organizing maps (SOM) to group children into "exposure profiles" that reflect discovered patterns of use for multiple SCPs.

Results: Children had lotions applied (43.0%) frequently, but "2-in-1" hair-care products (7.5%), sunscreens (5.9%), and oils (4.3%) infrequently. Use of lotions was associated with 1.17-fold [95% confidence interval (CI): 1.00, 1.34] greater mono-benzyl phthalate and oils with 2.86-fold (95% CI: 1.89, 4.31) greater monoethyl phthalate (MEP), 1.43-fold (95% CI: 1.09, 1.90) greater monobutyl phthalate (MBP), and 1.40-fold (95% CI: 1.22, 1.61) greater low-molecular-weight phthalates (LMW). Use of 2-in-1 haircare products was associated with 0.84-fold (95% CI: 0.72, 0.97) and 0.78-fold (95% CI: 0.62, 0.98) lesser mono(3-carboxypropyl) phthalate (MCPP) and MBP, respectively. Child's race/ethnic identity modified the associations of lotions with LMW, oils with MEP and LMW, sunscreen with MCPP, ointments with MEP, and hair conditioner with MCPP. SOM identified four distinct SCP-use exposure scenarios (i.e., profiles) within our population that predicted 1.09-fold (95% CI: 1.03, 1.15) greater mono-carboxy isononyl phthalate, 1.31-fold (95% CI: 0.98, 1.77) greater mono-2-ethyl-5-hydroxyhexyl terephthalate, 1.13-fold (95% CI: 0.99, 1.29) greater monoethylhexyl phthalate, and 1.04-fold (95% CI: 1.00, 1.09) greater diethylhexyl phthalate.

Discussion: We found that reported SCP use was associated with urinary phthalate/replacement metabolites in young children. These results may inform policymakers, clinicians, and parents to help limit children's exposure to developmental toxicants. https://doi.org/10.1289/EHP13937.

PubMed Disclaimer

Figures

Figure 1 is a graph, plotting V coordinate, ranging from 0.5 to 2.0 in increments of 0.5 (y-axis) across U coordinate, ranging from 1.0 to 2.5 in increments of 0.5 (x-axis) for lotions; hair oils; bar soap, liquid soap, and body wash; sunscreen; ointments; hand sanitizer; shampoo; conditioner; hair products other than shampoo, conditioner, or oil; 2 in 1 shampoo and hair conditioner products; 3 in 1 body wash, shampoo, and hair conditioner products; lip products; deodorant; other; products using only organic ingredients; phthalate-free products; paraben-free products; medicated products.
Figure 1.
Exposure continuum map describing frequencies of children of ECHO-FGS participants categorized into SCP-use exposure profiles using a self-organizing map (n=906) (numeric data in Table S11). Note: Exposure profile categories are defined based on the frequencies of participant responses to each SCP-use question and illustrated using radial bars labeled with letters indicating the average reported frequencies normalized to the range of reported frequencies in the study population; longer bars correspond to greater use. For example, exposure profiles 2 and 4 include children that reported greater use of lotions than children in exposure profiles 1 and 3. Cond., hair conditioner; Deod., deodorant; ECHO-FGS, Environmental Influences on Child Health Outcomes-Fetal Growth Study; Hair, hair products other than shampoo, conditioner, or oil; Hand., hand sanitizer; Lip., lip products; Med., medicated products; Oils, hair oil; Organic, products using only organic ingredients; Par-fr., paraben-free products; Pht-fr., phthalate-free products; SCP, personal care product; Soap, bar soap, liquid soap, and body wash; Sun., sunscreen; 2–1s, 2-in-1 shampoo and hair conditioner products; 3–1s, 3-in-1 body wash, shampoo, and hair conditioner products.
Figure 2 is a set of twenty-one error bar graphs titled mono-benzyl phthalate, mono-carboxy isononyl phthalate, mono-carboxy isooctyl phthalate, cyclohexane-1,2-dicarboxylic acid mono carboxyisooctyl ester, mono (3-carboxypropyl) phthalate, mono (2-ethyl-5-carboxypentyl) phthalate, mono-2-ethyl-5-carboxypentyl terephthalate, mono (2-ethyl-5-hydroxyhexyl) phthalate, mono-2-ethyl-5-hydroxyhexyl terephthalate, mono ethyl hexyl phthalate, mono (2-ethyl-5-oxohexyl) phthalate, monoethyl phthalate, cyclohexane-1,2-dicarboxylic acid mono hydroxyisononyl ester, mono-isobutyl phthalate, mono-isononyl phthalate, mono-n-butyl phthalate, di-isononyl cyclohexane-1,2-dicarboxylate, mono-n-butyl phthalate, di-2-ethylhexyl terephthalate, low molecular weight, high molecular weight, plotting relative difference in geometric means (95 percent confidence interval), ranging from 0.8 to 1.6 in increments of 0.2; 0.9 to 1.1 in increments of 0.1; 0.8 to 1.3 in increments of 0.1; 0.8 to 1.3 in increments of 0.1; 0.7 to 1.2 in increments of 0.1; 0.8 to 1.2 in increments of 0.2; 1.0 to 1.5 in increments of 0.5; 0.8 to 1.4 in increments of 0.2; 0.6 to 1.8 in increments of 0.3; 0.8 to 1.3 in increments of 0.1; 0.8 to 1.2 in increments of 0.2; 1.0 to 1.5 in increments of 0.5; 0.8 to 1.4 in increments of 0.2; 0.8 to 1.4 in increments of 0.2; 0.94 to 1.02 in increments of 0.02; 0.8 to 1.2 in increments of 0.2; 0.990 to 1.010 in increments of 0.005; 0.95 to 1.05 in increments of 0.05; 0.9 to 1.2 in increments of 0.1; 0.9 to 1.2 in increments of 0.1; and 0.9 to 1.2 in increments of 0.1 (y-axis) across Exposure category (reference group equals category 3), ranging from 1 to 2 in unit increments and 2 and 4 in increments of 2 (x-axis), respectively.
Figure 2.
Relationships between SCP-use exposure profile categories and urinary phthalate/replacement metabolite concentrations (ng/mL or nmol/L for composite sums) among children of ECHO-FGS participants (n=618) (numeric data in Table S12). Note: Multiple linear regression models adjusted for child’s urinary specific gravity, age (years), race/ethnic identity (NHB, Hispanic, NHW, or Asian/PI), sex assigned at birth (female/male), and body mass index (kg/m2), maternal education (completed secondary school yes or no), and season of urine collection (fall, winter, spring, or summer). We estimated the effect of membership in exposure category 1, 2, or 4 compared to exposure category 3 on the geometric mean urinary phthalate/replacement concentration (ng/mL or nmol/L for composite sums). The points on the graph represent the effect estimates for the relative differences in geometric mean concentrations, and the lines represent the 95% confidence intervals. CI, confidence interval; DEHP, diethylhexyl phthalate; DEHTP, di-2-ethylhexyl terephthalate; DINCH, di-isononyl cyclohexane-1,2-dicarboxylate; ECHO-FGS, Environmental Influences on Child Health Outcomes-Fetal Growth Study; LMW, low molecular weight; HMW, high molecular weight; MBP, mono-n-butyl phthalate; MBzP, mono-benzyl phthalate; MCiNP, mono-carboxy isononyl phthalate; MCiOP, mono-carboxy isooctyl phthalate; MCOCH, cyclohexane-1,2-dicarboxylic acid mono carboxyisooctyl ester; MCPP, mono (3-carboxypropyl) phthalate; MECPP, mono (2-ethyl-5-carboxypentyl) phthalate; MECPTP, mono-2-ethyl-5-carboxypentyl terephthalate; MEHHP, mono (2-ethyl-5-hydroxyhexyl) phthalate; MEHHTP, mono-2-ethyl-5-hydroxyhexyl terephthalate; MEHP, mono ethyl hexyl phthalate; MEOHP, mono (2-ethyl-5-oxohexyl) phthalate; MEP, monoethyl phthalate; MHNCH, cyclohexane-1,2-dicarboxylic acid mono hydroxyisononyl ester; MiBP, mono-isobutyl phthalate; MiNP, mono-isononyl phthalate; NHB, non-Hispanic black; NHW, non-Hispanic white; PI, Pacific Islander; SCP, skincare product.
Figure 2 is a set of twenty-one error bar graphs titled mono-benzyl phthalate, mono-carboxy isononyl phthalate, mono-carboxy isooctyl phthalate, cyclohexane-1,2-dicarboxylic acid mono carboxyisooctyl ester, mono (3-carboxypropyl) phthalate, mono (2-ethyl-5-carboxypentyl) phthalate, mono-2-ethyl-5-carboxypentyl terephthalate, mono (2-ethyl-5-hydroxyhexyl) phthalate, mono-2-ethyl-5-hydroxyhexyl terephthalate, mono ethyl hexyl phthalate, mono (2-ethyl-5-oxohexyl) phthalate, monoethyl phthalate, cyclohexane-1,2-dicarboxylic acid mono hydroxyisononyl ester, mono-isobutyl phthalate, mono-isononyl phthalate, mono-n-butyl phthalate, di-isononyl cyclohexane-1,2-dicarboxylate, mono-n-butyl phthalate, di-2-ethylhexyl terephthalate, low molecular weight, high molecular weight, plotting relative difference in geometric means (95 percent confidence interval), ranging from 0.8 to 1.6 in increments of 0.2; 0.9 to 1.1 in increments of 0.1; 0.8 to 1.3 in increments of 0.1; 0.8 to 1.3 in increments of 0.1; 0.7 to 1.2 in increments of 0.1; 0.8 to 1.2 in increments of 0.2; 1.0 to 1.5 in increments of 0.5; 0.8 to 1.4 in increments of 0.2; 0.6 to 1.8 in increments of 0.3; 0.8 to 1.3 in increments of 0.1; 0.8 to 1.2 in increments of 0.2; 1.0 to 1.5 in increments of 0.5; 0.8 to 1.4 in increments of 0.2; 0.8 to 1.4 in increments of 0.2; 0.94 to 1.02 in increments of 0.02; 0.8 to 1.2 in increments of 0.2; 0.990 to 1.010 in increments of 0.005; 0.95 to 1.05 in increments of 0.05; 0.9 to 1.2 in increments of 0.1; 0.9 to 1.2 in increments of 0.1; and 0.9 to 1.2 in increments of 0.1 (y-axis) across Exposure category (reference group equals category 3), ranging from 1 to 2 in unit increments and 2 and 4 in increments of 2 (x-axis), respectively.
Figure 2.
Relationships between SCP-use exposure profile categories and urinary phthalate/replacement metabolite concentrations (ng/mL or nmol/L for composite sums) among children of ECHO-FGS participants (n=618) (numeric data in Table S12). Note: Multiple linear regression models adjusted for child’s urinary specific gravity, age (years), race/ethnic identity (NHB, Hispanic, NHW, or Asian/PI), sex assigned at birth (female/male), and body mass index (kg/m2), maternal education (completed secondary school yes or no), and season of urine collection (fall, winter, spring, or summer). We estimated the effect of membership in exposure category 1, 2, or 4 compared to exposure category 3 on the geometric mean urinary phthalate/replacement concentration (ng/mL or nmol/L for composite sums). The points on the graph represent the effect estimates for the relative differences in geometric mean concentrations, and the lines represent the 95% confidence intervals. CI, confidence interval; DEHP, diethylhexyl phthalate; DEHTP, di-2-ethylhexyl terephthalate; DINCH, di-isononyl cyclohexane-1,2-dicarboxylate; ECHO-FGS, Environmental Influences on Child Health Outcomes-Fetal Growth Study; LMW, low molecular weight; HMW, high molecular weight; MBP, mono-n-butyl phthalate; MBzP, mono-benzyl phthalate; MCiNP, mono-carboxy isononyl phthalate; MCiOP, mono-carboxy isooctyl phthalate; MCOCH, cyclohexane-1,2-dicarboxylic acid mono carboxyisooctyl ester; MCPP, mono (3-carboxypropyl) phthalate; MECPP, mono (2-ethyl-5-carboxypentyl) phthalate; MECPTP, mono-2-ethyl-5-carboxypentyl terephthalate; MEHHP, mono (2-ethyl-5-hydroxyhexyl) phthalate; MEHHTP, mono-2-ethyl-5-hydroxyhexyl terephthalate; MEHP, mono ethyl hexyl phthalate; MEOHP, mono (2-ethyl-5-oxohexyl) phthalate; MEP, monoethyl phthalate; MHNCH, cyclohexane-1,2-dicarboxylic acid mono hydroxyisononyl ester; MiBP, mono-isobutyl phthalate; MiNP, mono-isononyl phthalate; NHB, non-Hispanic black; NHW, non-Hispanic white; PI, Pacific Islander; SCP, skincare product.

References

    1. Gore AC, Chappell VA, Fenton SE, Flaws JA, Nadal A, Prins GS, et al. . 2015. EDC-2: the endocrine society’s second scientific statement on endocrine-disrupting chemicals. Endocr Rev 36(6):E1–E150, PMID: 26544531, 10.1210/er.2015-1010. - DOI - PMC - PubMed
    1. Braun JM. 2017. Early-life exposure to EDCs: role in childhood obesity and neurodevelopment. Nat Rev Endocrinol 13(3):161–173, PMID: 27857130, 10.1038/nrendo.2016.186. - DOI - PMC - PubMed
    1. Minatoya M, Kishi R. 2021. A review of recent studies on bisphenol a and phthalate exposures and child neurodevelopment. Int J Environ Res Public Health 18(7):3585, 10.3390/ijerph18073585. - DOI - PMC - PubMed
    1. Radke EG, Braun JM, Nachman RM, Cooper GS. 2020. Phthalate exposure and neurodevelopment: a systematic review and meta-analysis of human epidemiological evidence. Environ Int 137:105408, PMID: 32045779, 10.1016/j.envint.2019.105408. - DOI - PMC - PubMed
    1. Li MC, Chen CH, Guo YL. 2017. Phthalate esters and childhood asthma: a systematic review and congener-specific meta-analysis. Environ Pollut 229:655–660, PMID: 28692937, 10.1016/j.envpol.2017.06.083. - DOI - PubMed

LinkOut - more resources