Skip to main content
Environmental Health Perspectives logoLink to Environmental Health Perspectives
. 2024 Feb 2;132(2):027001. doi: 10.1289/EHP13882

Personal Care Product Use during Puberty and Incident Breast Cancer among Black, Hispanic/Latina, and White Women in a Prospective US-Wide Cohort

Mandy Goldberg 1, Che-Jung Chang 1, Kemi Ogunsina 1, Katie M O’Brien 1, Kyla W Taylor 2, Alexandra J White 1, Dale P Sandler 1,
PMCID: PMC10836586  PMID: 38306193

Abstract

Background:

Some personal care products (PCPs) contain endocrine-disrupting chemicals that may affect breast cancer (BC) risk. Patterns of use vary by race and ethnicity. Use often starts in adolescence, when rapidly developing breast tissue may be more susceptible to environmental carcinogens. Few studies have examined associations of BC with PCP use during this susceptible window.

Objectives:

We characterized race and ethnicity-specific patterns of PCP use at 10–13 years of age and estimated associations of use with incident BC.

Methods:

At enrollment (2003–2009), Sister Study participants (n=4,049 Black, 2,104 Latina, and 39,312 White women) 35–74 years of age reported use of 37 “everyday” PCPs during the ages of 10–13 y (did not use, sometimes, or frequently used). We conducted race and ethnicity-specific latent class analyses to separately identify groups of women with similar patterns of beauty, hair, and skincare/hygiene product use. We estimated hazard ratios (HRs) and 95% confidence intervals (CIs) for associations of identified PCP classes and single products with incident BC using Cox proportional hazards regression.

Results:

During a mean follow-up time of 10.8 y, 280 Black, 128 Latina, and 3,137 White women were diagnosed with BC. Classes of adolescent PCP use were not clearly associated with BC diagnosis among Black, Latina, or White women. HRs were elevated but imprecise for frequent nail product and perfume use in Black women (HR=1.34; 95% CI: 0.85, 2.12) and greater hair product use in Black (HR=1.28; 95% CI: 0.91, 1.80) and Latina (HR=1.42; 95% CI: 0.81, 2.48) women compared with lighter use. In single-product models, we observed higher BC incidence associated with frequent use of lipstick, nail products, pomade, perfume, makeup remover, and acne/blemish products in at least one group.

Discussion:

This work provides some support for the hypothesis that PCP use during puberty is associated with BC risk. More research is needed to confirm these novel findings. https://doi.org/10.1289/EHP13882

Introduction

Many personal care products (PCPs) contain endocrine-disrupting chemicals (EDCs), including phthalates, parabens, and phenols,14 that may affect breast cancer (BC) risk.57 Although many EDCs used in PCPs are nonpersistent,8 women can be chronically exposed through regular use. Laboratory studies report that EDCs in PCPs are present in breast tissue,9 can alter hormone signaling and disrupt mammary gland development in rodents,5,10 and stimulate proliferation, migration, and invasive activity in human BC cell lines.5,9 However, epidemiological evidence is inconclusive, with conflicting findings reported across studies that have examined biomarkers of chemicals found in PCPs,1117 use of multiple PCPs,1820 or use of individual products21 in relation to BC risk.

The breast is more vulnerable to environmental exposures during periods of rapid development, including during puberty.22,23 Few prior epidemiological studies have measured PCP-related exposures during this window of BC susceptibility.5 Puberty may be a particularly relevant period for EDC exposure through PCPs because product use is common in adolescence.24,25 Previous studies have linked adolescent use of hair straighteners or relaxers to increased BC risk2628 but have not examined the contributions of commonly used “everyday” PCPs during puberty, including makeup, hair, skincare, and hygiene products, individually or in combination, to BC incidence.

Studies have demonstrated clear differences in PCP use patterns in women by race and ethnicity.2931 More frequent use of certain hair (e.g., relaxers and straighteners), skin (e.g., skin lighteners), and intimate care products (e.g., talcum powder, douche) by women of color have been attributed to structural racism, discrimination, racialized beauty norms, and targeted marketing campaigns under the environmental injustice of beauty conceptual framework.32,33 Products marketed to Black women have been found to have different chemical composition and contain higher concentrations of EDCs than those marketed to White women.34 These differences likely contribute to greater body burdens of PCP-related chemicals observed in Black and Hispanic/Latina women compared with non-Hispanic White women in the United States.35,36 For some chemicals commonly found in PCPs, including monoethyl phthalate and methyl and propyl paraben, disparities in biomarker concentrations between non-Hispanic Black and White women were greater in childhood (<12 years of age) and adolescence (12–19 years of age) than in adulthood,35 which may reflect the young age at initiation of PCP use by Black girls.36 Thus, racial and ethnic differences in PCP use is a potentially modifiable factor that may contribute to BC disparities.3739

We examined associations of use of a comprehensive list of everyday PCPs during the ages of 10–13 y, coinciding with the pubertal window of susceptibility, with BC incidence separately among Black or African American, non-Black Hispanic/Latina, and non-Hispanic/Latina White women (hereafter, Black, Latina, and White women, respectively) in the Sister Study, a prospective US-wide cohort. To our knowledge, this is the first epidemiological study to investigate use of these everyday PCPs during puberty in relation to BC risk; we and others have previously considered only adult use of these products.1821 For our primary analyses, we identified groups of women with similar patterns of beauty, hair, and skincare/hygiene product use through race- and ethnicity-specific latent class analyses and examined the associations of product use classes with incident BC. We hypothesized that classes representing greater product use (e.g., more frequent use of a larger number of product types) during puberty would be associated with increased BC incidence and that associations may vary by estrogen-related factors, including menopausal status, estrogen receptor (ER) status of the tumor, and age at onset of pubertal breast development (thelarche). Multiple PCPs are frequently used together, and the latent class approach captures real-life use patterns, minimizes confounding by use of correlated products, and accounts for the greater EDC burden associated with use of more products.8,24,40 We also conducted single-product analyses of incident BC to complement our latent class analyses and ascertain individual products that may warrant additional research.

Methods

Study Sample

The Sister Study is a prospective cohort of 50,884 women enrolled between 2003 and 2009 (for more details, see Sandler et al.41). Women were eligible to join if they lived in a US state or Puerto Rico, were between 35 and 74 years of age, and had a sister with a BC diagnosis but did not have a personal history of BC themselves.

Women completed a computer-assisted telephone interview and self-administered questionnaires at enrollment to assess demographics, reproductive and medical history, and lifestyle factors. A PCP use questionnaire was self-administered at enrollment. Women are followed prospectively with annual updates and comprehensive follow-up questionnaires administered every 3 y. Approximately 85% of participants completed the most recent study activity. This analysis used Sister Study Data Release 9.1, including follow-up data up to 30 September 2019. The institutional review board of the National Institutes of Health approved the study. All participants provided written, informed consent.

Because we stratified by race and ethnicity, we did not include participants with unknown race/ethnicity (n=15) or who did not self-identify as Black, Latina, or White (n=1,334) owing to the small numbers of women who identified as having other racial and ethnic backgrounds (Figure S1), as further described below. Among Black (n=4,600), Latina (n=2,377), and White (n=42,558) participants, we excluded women who withdrew their data (n=3), did not complete the PCP questionnaire (n=902), or completed an earlier version of the questionnaire that was not specific to PCP use at 10–13 years of age (n=2,236). We also excluded women who were diagnosed with BC prior to, at the same age as, or at unknown timing relative to the completion of all baseline study components (n=84), had uncertain BC diagnoses (n=5), lacked prospective follow-up data (n=226), or were missing data for childhood family income level or maximum education level in the household at 13 years of age, which we included as confounders (n=614). The analytic sample included 4,049 Black, 2,104 Latina, and 39,312 White women.

Exposure Assessment: PCP Use during Puberty

At enrollment, women reported how often they used 45 types of PCPs during the ages of 10–13 y. Response options for all products were “did not use,” “sometimes,” “frequently,” and “don’t know.” We were interested in products that may be applied daily, representing a chronic source of EDC exposure. We included 37 products that we defined as everyday PCPs based on the potential for daily use, including 13 beauty products, 6 hair products, and 18 skincare/hygiene products (Figure 1). We did not include 7 hair products that are used periodically (permanent hair dye, semipermanent hair dye, hair color rinses, bleach, frost or highlights, straighteners/relaxers, and permanent body waves). We also did not include douching because the questionnaire did not distinguish between douching with water or chemical douche products. Women also reported their PCP use in the 12 months before enrollment, which we did not include in our analyses because adult use would be a mediator of associations between PCP use during puberty and BC risk.

Figure 1.

Figure 1 is a set of nine horizontal stacked bar graphs. On the left, the three graphs are titled Black or African American; at the center, the three graphs are titled Non-Black Hispanic or Latina; and on the left, the three graphs are titled Non-Hispanic White, each are plotting talcum powder on other areas, talcum powder on genital area, talcum powder under arms, mouthwash or rinse, blemish or acne products, face masks, cleansing cream, face cream or moisturizer, deodorant or antiperspirant, shaving cream or gel, bath or shower gel, self-tanning products, skin lighteners, petroleum jelly, baby oil or mineral-based oils, foot lotions or creams, hand lotions or creams, body lotions or creams under Skincare or hygiene; hair food, pomade or hair grease, hair styling gel or mousse, hair spray, conditioner or rinse, shampoo under Hair; perfume or cologne, artificial nails or fill-ins, cuticle cream, nail polish remover, nail polish, makeup remover, blush or rouge, foundation, lip moisturizer, lipstick, eye liner, eye shadow, mascara under Beauty (y-axis) across percent of participants, ranging from 0 to 100 in increments of 25 (x-axis) for frequency of use, did not use (lightest shade of blue), sometimes (middle shade of blue), and frequently (darkest shade of blue), respectively.

Frequency of self-reported personal care product use during the ages of 10–13 y by race and ethnicity in the Sister Study. Darker shading indicates more frequent product use. Numbers indicate the percentage of participants in each frequency category. Categories without a number include <3% of participants.

Assessment of Race and Ethnicity

We asked women to self-identify their race by choosing one or more of the following: American Indian or Alaska Native, Asian, Black or African American, Native Hawaiian or other Pacific Islander, or White. Women were also asked if they considered themselves to be Hispanic or Latina. We categorized all women who identified as Black or African American as Black, including women who identified as Black and one or more other races or Black and Latina, under the assumption that multiracial or multiethnic Black women may experience some of the same sociocultural influences, such as structural racism, discrimination, and targeted marketing, that affect PCP use. We categorized women who reported that they were Hispanic or Latina and did not identify as Black or African American as Latina. Women who identified as White and did not consider themselves as Hispanic or Latina were categorized as White. Women who identified as non-Hispanic and a) Asian/Pacific Islander (n=341), b) American Indian/Alaskan native (n=93), or c) with two or more of American Indian/Alaskan native, Asian/Pacific Islander, and White (n=900), were excluded because the very low numbers of women in these groups precluded stratified analyses.

Covariate Assessment

Potential confounders were identified a priori. We categorized participant birth year in approximate 10-y intervals (1928–1939, 1940–1949, 1950–1959, and 1960–1974) as a proxy for potential changes in product use patterns and the composition of PCPs on the market over time. Participants were asked to characterize their family’s income level during the majority of their time growing up using the response options of “well off,” “middle income,” “low income,” or “poor.” We categorized the participant’s report of the highest level of education in the household when they were 13 years of age as less than high school degree, high school degree or equivalent, some college or technical degree, or 4-y college degree or higher. Participants were asked how old they were when they first noticed their breasts developing, which we used to categorize age at thelarche as <10, 10–13, and >13 y. We considered reports of thelarche at 21 years of age as implausible and set them to missing (n=29).42 Participants reported if they considered themselves to be lighter, heavier, or the same weight as their peers when they were 10 y old. Childhood PCP use could affect body size and timing of thelarche, which in turn could influence subsequent use of PCPs. Therefore, we did not include age at thelarche or relative childhood weight as covariates in our primary multivariable-adjusted models because these factors could be confounders or mediators of associations between PCP use during the 10- to 13-years-of-age period and incident BC depending on their timing relative to the time of product use queried. We also did not include BC risk factors that postdate the exposure assessment period of 10–13 y (e.g., age at menarche, parity, age at first birth) because these factors are also potential mediators.

Outcome Assessment: Incident BC

Our primary outcome was incident BC [invasive or ductal carcinoma in situ (DCIS)]. We confirmed self-reported diagnoses and obtained information on tumor invasiveness and ER status through medical records when available (>80% of cases). We used self-reports when records were unavailable given that agreement between self-reports and medical records has been high in the cohort (positive predictive value for total and ER-positive cancer of >99%).43

Statistical Analysis

We examined the distributions of participant characteristics among the analytic samples of Black, Latina, and White participants, as well as those excluded from the analyses. We grouped products by type (beauty, hair, skincare/hygiene) and summed the total number of products ever used within each type for each participant, assuming that participants did not use products for which they were missing response data. We visualized the distribution of frequency of use of each product by race and ethnicity through stacked bar charts. We estimated Spearman’s rank correlation coefficients (rho) between product use frequencies (coded as ordinal variables) and birth cohort (ordinal, increasing with calendar time), childhood socioeconomic indicators [ordinal from lower to higher socioeconomic status (SES)], and age at thelarche (in years, continuous) within each racial and ethnic group. We estimated pairwise correlations for use of the 37 included PCPs among Black, Latina, and White women using Spearman’s rho.

We used race and ethnicity-specific latent class analysis (LCA) to identify groups of women with similar patterns of use of beauty, hair, and skincare/hygiene products using PROC LCA in SAS (version 9.4; SAS Institute, Inc.).44 For each LCA, we did not include products that were used by <2% of participants (see Table S1 for included products). We dichotomized products if <2% of women reported one of the use categories. Missing data on frequency of use ranged from 0.5% to 7% per product (Table S2). We included participants with missing individual product data in the LCAs under the assumption that data were missing at random. We excluded the small number of participants missing data on all included products from the product type group LCA and subsequent models of BC incidence (see Table S1). We estimated up to five LCA models for each product type group, with two to six latent classes, and compared model fit using Akaike’s information criterion and the Bayesian information criterion.44,45 We also considered entropy and the interpretability of the classes in selecting the final model and required a minimum class membership probability of at least 5% to allow for sufficient BC cases in each class. Participants were assigned to the class with the highest posterior probability of membership.46 We labeled classes based on the item response probabilities of the included products and examined the median number of products used by participants in each latent class.

We used Cox proportional hazards regression with age as the timescale to estimate hazard ratios (HRs) and 95% confidence intervals (CIs) for the associations of race and ethnicity-specific latent classes of beauty, hair, and skincare/hygiene product use with incident BC. Women accrued person-time from age at enrollment until age at diagnosis, with censoring at end of study follow-up (30 September 2019), loss to follow-up, or death. We tested for violations of the proportional hazards assumption using Wald tests of exposure-by-time interaction terms. Any violations of the assumption are indicated in table footnotes. We examined models adjusted only for age as the timescale and multivariable-adjusted models, with the latter including terms for birth cohort, childhood family income, and maximum household education level at 13 years of age. In sensitivity analyses, we additionally adjusted for age at thelarche and relative childhood weight. For each analysis, we used the latent class representing the lowest product use, based on the item response probabilities of the included products and the median number of products used in each class, as the reference.

We examined differences in associations between classes of PCP use and incident BC by BC characteristics. We considered differences by time-varying menopausal status and tested for statistical heterogeneity using a Wald test of the product use–menopause interaction terms. We used fully adjusted joint Cox models stratified by type to estimate associations and test for statistical heterogeneity by ER status and invasiveness.47 We included invasive and DCIS cases in models of ER status and censored women with the alternative subtype or missing subtype information at age at diagnosis. For models of invasive and DCIS disease, women with the alternate type or missing invasiveness information were censored at age at diagnosis. We estimated associations for strata that included at least 5 cases in each latent class.

We examined timing of thelarche as a potential modifier under the hypothesis that the effect of exogenous estrogens may differ depending on endogenous estrogen concentrations and breast maturation. We stratified models of classes of PCP use in White women by age at thelarche and tested for statistical heterogeneity using a Wald test of the product use–age at thelarche interaction terms. We did not stratify by age at thelarche in Black or Latina women because there were <5 cases in some classes.

We estimated multivariable-adjusted associations of use of individual products with incident BC in race and ethnicity-stratified Cox models. For these single-product models, we combined “frequently” and “sometimes” use categories into an “any-use” category if there were <5 cases in the frequently used group. We did not estimate associations for products with <5 any-use cases. “Nonusers” were used as the referent group if there were at least 10 cases in this category. Because single-product models may be confounded by use of other correlated products, we conducted additional analyses in which we adjusted for the total number of products used within the product type group (e.g., we adjusted for the number of beauty products ever used in the 10- to 13-years-of-age period in analyses of individual beauty products). We excluded participants with missing data on the product of interest from single-product models.

To rule out an influence of adolescent straightener/relaxer use, previously linked with premenopausal BC in this cohort,26 we conducted sensitivity analyses of associations with everyday hair product classes restricted to women who did not use straighteners/relaxers during the 10- to 13-years-of-age period. Because women may use pomade prior to applying these products,48 we examined correlations of straightener/relaxer and pomade use and restricted pomade models to nonstraightener/relaxer users.

We conducted sensitivity analyses for the associations of latent classes and single products with incident BC among Black participants excluding bi- and multiracial Black women and Black Latinas because types of products used may vary for women who identify as bi- or multiracial or multiethnic29,31 and there may be differences in the brands used and associated chemical constituents within the same broad types of products.

We used robust variance estimates to account for within-family clustering. We conducted analyses using SAS (version 9.4; SAS Institute, Inc.) and created figures in R (version 4.2.2; R Development Core Team).

Results

Study Population Characteristics

Distributions of demographic characteristics were similar between the analytic samples of Black, Latina, and White participants and those that were excluded from the analyses (Table S3). During a mean follow-up of 10.8 y, 280 Black, 128 Latina, and 3,137 White women were diagnosed with BC (Table 1). Early life demographic characteristics were similar among Black and Latina participants, although the proportion of participants who reported that the highest educational level completed by an adult in their household when they were 13 years of age was less than a high school degree was higher among Latinas. Compared with Black or Latina women, White women were older at baseline, more likely to grow up in a well-off or middle-income household and a household with educational attainment of a 4-y college degree or higher, and less likely to experience thelarche before 10 years of age. The median number of products used during the 10- to 13-years-of-age period was 13 among Black, 9 among Latina, and 10 among White women. The median number of beauty products used in adolescence was 3 in all groups. The median number of hair products used in adolescence was 3 among Black women and 2 among Latina and White women, whereas the median number of skincare/hygiene products used was 7 among Black women, 4 among Latinas, and 5 among White women.

Table 1.

Participant characteristics among eligible Black or African American, non-Black Hispanic/Latina, and non-Hispanic White women in the Sister Study cohort (N=45,465).

Characteristic Black or African American Non-Black Hispanic/Latina Non-Hispanic White
Participants (n) 4,049 2,104 39,312
Cases (n) 280 128 3,137
Follow-up time [y (mean±SD)] 9.9±2.8 9.9±2.9 11.0±2.8
Age at baseline [y (mean±SD)] 53.6±8.3 53.2±9.0 56.1±8.9
Birth cohort [n (%)]
 1928–1939 191 (5) 120 (6) 4,982 (13)
 1940–1949 1,065 (26) 529 (25) 13,333 (34)
 1950–1959 1,709 (42) 820 (39) 14,451 (37)
 1960–1974 1,084 (27) 635 (30) 6,546 (17)
Family income level growing up [n (%)]
 Well off 118 (3) 108 (5) 2,711 (7)
 Middle income 1,683 (42) 847 (40) 24,789 (63)
 Low income 1,488 (37) 702 (33) 9,553 (24)
 Poor 760 (19) 447 (21) 2,259 (6)
Highest level of education in household at 13 years of age [n (%)]
 Less than high school degree 1,513 (37) 1,196 (57) 5,549 (14)
 High school degree or equivalent 1,437 (35) 394 (19) 14,460 (37)
 Some college or technical degree 637 (16) 215 (10) 7,714 (20)
 4-y college degree or higher 462 (11) 299 (14) 11,589 (29)
Age at thelarche [y; n (%)]
<10 266 (7) 123 (6) 1,193 (3)
 10–13 2,910 (73) 1,601 (77) 31,108 (80)
>13 810 (20) 346 (17) 6,572 (17)
 Missing 63 34 439
Weight relative to peers at 10 years of age [n (%)]
 Lighter 1,696 (42) 869 (42) 13,189 (34)
 Same weight 1,705 (42) 978 (47) 18,597 (47)
 Heavier 626 (16) 245 (12) 7,430 (19)
 Missing 22 12 96
Number of products ever used from 10 to 13 years of age [median (25th, 75th percentile)]
 Personal care products 13 (9, 16) 9 (5, 15) 10 (6, 15)
 Beauty products 3 (1, 4) 3 (1, 5) 3 (1, 5)
 Hair products 3 (2, 4) 2 (1, 3) 2 (1, 3)
 Skincare/hygiene products 7 (5, 9) 4 (2, 7) 5 (2, 7)

Note: Column percentages are displayed. Missing data are not included in calculation of percentages. Participants with missing data on family income level growing up and highest level of education in household at 13 years of age were excluded (see Figure S1). SD, standard deviation.

PCP Use during the 10- to 13-Years-of-Age Period by Race and Ethnicity

Perfume, nail polish and polish remover, and lip moisturizers were the most commonly used beauty products during the 10- to 13-years-of-age period, with the highest prevalence of nail polish use reported by Black women and the highest prevalence of perfume use reported by Latina women (Figure 1). Except for lipstick, <20% of Latina and White women and 10% of Black women reported any adolescent use of each makeup product. Almost all Black women (94%) used pomade or hair grease and 27% used hair food in adolescence, whereas these products were used by a small proportion of Latina women and few White women. Hair spray or gel were used by a higher proportion of Latina (36% and 16%, respectively) and White (40% and 16%) participants than Black participants (17% and 11%) during the 10- to 13-years-of-age period. Compared with Latina and White women, Black women were more frequent adolescent users of most skincare/hygiene products, particularly lotions or creams, oils, and petroleum jelly. Talcum powder was also used more frequently by Black women during adolescence.

Correlations between product use frequencies during the 10- to 13-years-of-age period and covariates of interest were generally weak in magnitude but exhibited similar patterns across racial and ethnic groups (Figure S2, Excel Table S1). Use of most products during the 10- to 13-years-of-age period was inversely correlated with age at thelarche, with the strongest correlations observed for deodorant, perfume, and makeup products. Product use increased with birth cohort, except for lipstick and talc products, which were used less frequently by women born in later years. Product use tended to increase with family income and household education.

Patterns of correlations between product use frequencies during the 10- to 13-years-of-age period were similar among Black, Latina, and White women (Figures S3–S5, Excel Tables S2–S4). Use of products within a category (beauty, hair, and skincare/hygiene) were positively correlated. Correlations of products across categories were smaller in magnitude. Spearman’s rho ranged from 0.4 to 0.7 for most makeup products, but the correlation was 0.9 for nail polish and nail polish remover. Hair spray and hair gel use were positively correlated in all groups (rho=0.4), whereas pomade/hair grease and hair food use were correlated in Latina women (rho=0.4). Use of talc products on different areas of the body was positively correlated (rho=0.30.5), as was lotion use (rho=0.60.7 for body and hand lotion).

Latent Classes of PCP Use during the 10- to 13-Years-of-Age Period and Incident BC

Among Black women, we selected the four-class model for beauty products, three-class model for hair products, and four-class model for skincare/hygiene products based on model fit (Table S1) and interpretability (Figure S6, Excel Table S5). Latent classes of product use were not clearly associated with BC risk (Table 2). Compared with the class characterized by some perfume and lip moisturizer use, the estimated HR for the frequent nail product and perfume use class was 1.34 (95% CI: 0.85, 2.12). HRs were positive in direction but CIs were wide for classes representing frequent use of shampoo, conditioner, and pomade and some use of hair spray, hair gel, and hair food (HR=1.28; 95% CI: 0.91, 1.80) and frequent shampoo, conditioner, and pomade use (HR=1.24; 95% CI: 0.94, 1.63) compared with frequent pomade and some shampoo use only, and for frequent lotions, some moisturizers, and little talc use (HR=1.22; 95% CI: 0.85, 1.73) compared with some use of lotions and petroleum jelly.

Table 2.

Associations between latent classes of self-reported personal care product use during the 10- to 13-years-of-age period and incident breast cancer among Black or African American, non-Black Hispanic/Latina, and non-Hispanic White women in the Sister Study.

Race and ethnicity-specific latent class Number of products used (median)a Person-years n cases Age-adjusted HR (95% CI)b Multivariable-adjusted HR (95% CI)c
Black or African American women (n=4,049)
Latent classes of beauty product use from 10 to 13 years of age
 Any makeup, nail product, and perfume use 7 3,610 24 1.00 (0.64, 1.55) 1.03 (0.66, 1.60)
 Frequent nail product and perfume use 4 2,568 23 1.33 (0.84, 2.11) 1.34 (0.85, 2.12)
 Some nail product and perfume use 3 20,104 127 0.89 (0.68, 1.15) 0.89 (0.69, 1.15)
 Some use of perfume and lip moisturizer 1 13,931 106 1 (Ref) 1 (Ref)
Latent classes of hair product use from 10 to 13 years of age
 Frequent shampoo, conditioner, and pomade and some hair spray, hair gel, and hair food 5 7,317 52 1.25 (0.89, 1.74) 1.28 (0.91, 1.80)
 Frequent shampoo, conditioner, and pomade 3 15,197 106 1.22 (0.93, 1.59) 1.24 (0.94, 1.63)
 Frequent pomade and some shampoo 2 17,565 122 1 (Ref) 1 (Ref)
Latent classes of skincare/hygiene product use from 10 to 13 years of aged
 Frequent moisturizers, including lotions, oil, and petroleum jelly, and some cleanser, hygiene products, and talc use 10 10,761 69 1.02 (0.71, 1.47) 1.05 (0.73, 1.52)
 Frequent lotions, some use of other moisturizers, and little talc use 7 10,607 78 1.19 (0.84, 1.69) 1.22 (0.85, 1.73)
 Some moisturizers, including lotions, oil, and petroleum jelly, and talc use 7 11,444 81 1.02 (0.72, 1.44) 1.02 (0.72, 1.44)
 Some use of lotions and petroleum jelly 3 7,401 52 1 (Ref) 1 (Ref)
Non-Black Hispanic/Latina women (n=2,104)
Latent classes of beauty product use from 10 to 13 years of age
 Frequent nail product and perfume and any makeup use 9 1,240 8 1.15 (0.54, 2.42) 1.17 (0.55, 2.50)
 Some nail product and perfume and any makeup use 7 3,293 16 0.85 (0.48, 1.49) 0.87 (0.49, 1.53)
 Some nail product and perfume and little makeup use 3 7,203 52 1.25 (0.85, 1.83) 1.27 (0.86, 1.88)
 Some use of perfume and lip moisturizer 1 9,036 52 1 (Ref) 1 (Ref)
Latent classes of hair product use from 10 to 13 years of age
 Frequent shampoo and conditioner and some hair spray, hair food, hair gel, and pomade 3 7,495 45 1.39 (0.81, 2.41) 1.42 (0.81, 2.48)
 Frequent shampoo and conditioner 2 8,973 64 1.62 (0.96, 2.73) 1.62 (0.96, 2.74)
 Some shampoo 1 4,234 19 1 (Ref) 1 (Ref)
Latent classes of skincare/hygiene product use from 10 to 13 years of age
 Frequent lotions and some oil, petroleum jelly, cleanser, hygiene products, and talc use 10 4,067 20 0.73 (0.43, 1.24) 0.72 (0.41, 1.26)
 Frequent lotions, some use of other moisturizers, and little talc use 5 6,344 48 1.10 (0.73, 1.67) 1.11 (0.73, 1.68)
 Some moisturizers, including lotions, oil, and petroleum jelly, and talc use 5 4,013 16 0.57 (0.32, 1.01) 0.57 (0.32, 1.02)
 Little use of any products 1 6,322 44 1 (Ref) 1 (Ref)
Non-Hispanic White women (n=39,312)
Latent classes of beauty product use from 10 to 13 years of age
 Any makeup, nail product, and perfume use 8 90,492 603 1.01 (0.91, 1.12) 1.01 (0.91, 1.12)
 Nail product and perfume and little makeup use 4 180,610 1,325 1.00 (0.93, 1.08) 1.00 (0.92, 1.08)
 Some use of perfume and lip moisturizer 1 160,614 1,209 1 (Ref) 1 (Ref)
Latent classes of hair product use from 10 to 13 years of aged
 Frequent shampoo, conditioner, and hair spray and some hair gel 4 25,479 179 1.06 (0.90, 1.24) 1.06 (0.90, 1.24)
 Frequent shampoo and conditioner and some hair spray use 3 113,949 814 1.04 (0.96, 1.13) 1.04 (0.95, 1.13)
 Frequent shampoo and conditioner use 2 68,891 443 1.00 (0.89, 1.11) 1.00 (0.89, 1.12)
 Frequent shampoo and some conditioner 1 222,820 1,697 1 (Ref) 1 (Ref)
Latent classes of skincare/hygiene product use from 10 to 13 years of age
 Frequent moisturizers, including lotions and oil, some petroleum jelly, cleanser, hygiene products, and talc use 10 67,010 446 0.96 (0.85, 1.07) 0.95 (0.85, 1.07)
 Some moisturizers, including lotions and oil, and talc use 7 81,612 581 0.93 (0.84, 1.03) 0.93 (0.84, 1.03)
 Some moisturizers, including lotions and oil, little talc use 5 146,826 1,050 0.98 (0.90, 1.07) 0.98 (0.90, 1.07)
 Little use of any products 2 136,291 1,060 1 (Ref) 1 (Ref)

Note: CI, confidence interval; HR, hazard ratio; Ref, reference.

a

Sum of the number of products used within each product type group (beauty, hair, skincare/hygiene, respectively).

b

Adjusted for age as the timescale.

c

Adjusted for birth cohort in 10-y intervals, family income level growing up (well off, middle income, low income, poor), and maximum household education level at 13 years of age (less than high school, high school graduate or equivalent, some college or technical school, 4-y degree or higher) in addition to age as the timescale.

d

Proportional hazards assumption violated for exposure in multivariable model (p<0.05).

Among Latina women, our final LCA models included four classes for beauty products, three classes for hair products, and four classes for skincare/hygiene products (Figure S7, Excel Table S6). The HR for frequent use of shampoo and conditioner and some use of hair spray, hair food, hair gel, and pomade relative to some shampoo use was 1.42 (95% CI: 0.81, 2.48) and the HR for frequent shampoo and conditioner use was 1.62 (95% CI: 0.96, 2.74) (Table 2). There were no clear patterns for associations with classes of beauty or skincare/hygiene product use. The HR was inverse for some use of some moisturizers and talc products (HR=0.57; 95% CI: 0.32, 1.02) compared with little use of any skincare/hygiene products.

Among White women, we identified three classes for beauty products, four classes for hair products, and four classes for skincare/hygiene products based on the final LCA model (Figure S8, Excel Table S7). HRs for BC incidence were all close to 1 for beauty, hair, or skincare/hygiene product use classes (Table 2). Results were similar in models additionally adjusted for age at thelarche and relative childhood weight among Black, Latina, and White women (Table S4).

There was no clear heterogeneity by menopausal status in Black and White women (Table S5). We did not observe strong differences by ER status (Table S6). Although associations for hair product use classes were farther from the null for ER-negative [HR=1.49 (95% CI: 0.63, 3.48) for frequent shampoo, conditioner, and pomade and some hair spray, hair gel, and pomade use and HR=1.58 (95% CI: 0.82, 3.03) for frequent shampoo, conditioner, and pomade use, respectively] than ER-positive cancer [HR=1.22 (95% CI: 0.78, 1.91) and HR=1.22 (95% CI: 0.84, 1.77), respectively] in Black women, estimates were based on small numbers of ER-negative cancers and were not statistically different from each other [p for heterogeneity (phet)=0.80]. We observed some differences in associations of classes of hair product use and BC incidence by tumor invasiveness (Table S7). Frequent use of shampoo, conditioner, and pomade and some use of hair spray, hair gel, and pomade was associated with 52% higher incidence of invasive tumors (95% CI: 1.04, 2.23) in Black women, whereas the estimated HR was inverse for DCIS (HR=0.68; 95% CI: 0.32, 1.46; phet=0.12). We observed a similar pattern for frequent use of shampoo, conditioner, and hair spray and some use of hair gel in White women [HR=1.17 (95% CI: 0.98, 1.39) for invasive and HR=0.72 (95% CI: 0.49, 1.06) for DCIS; phet=0.01]. The HR for frequent nail product and perfume use among Black women was farther from the null in analyses of invasive disease (HR=1.53; 95% CI: 0.90, 2.59), as was the HR for frequent nail product and perfume and any makeup use among Latinas (HR=1.56; 95% CI: 0.72, 3.35). Among White women, we did not observe statistical differences by timing of thelarche (Table S8), although we observed a suggestively higher incidence associated with the frequent use of shampoo, conditioner, and hair spray and some use of hair gel class (HR=1.38; 95% CI: 0.91, 2.09) and the frequent shampoo and conditioner and some hair spray use class (HR=1.24; 95% CI: 0.98, 1.56) among women with late thelarche.

Use of Individual Products during the 10- to 13-Years-of-Age Period and Incident BC

Frequent use of lipstick during the 10- to 13-years-of-age period was associated with higher BC incidence among Black (HR=1.91; 95% CI: 1.09, 3.32) and White (HR=1.22; 95% CI: 1.04, 1.44) women compared with nonuse, whereas the HR was 1.26 among Latinas (95% CI: 0.61, 2.60) (Table 3). Frequent use of makeup remover was associated with a 60% higher incidence in White women (95% CI: 1.10, 2.32), whereas the HR for any use was 1.41 among Latinas (95% CI: 0.78, 2.55). Among Black women, frequent use of cuticle cream was associated with higher BC risk (HR=2.87; 95% CI: 1.25, 6.57), whereas the HR was 1.23 (95% CI: 0.81, 1.86) for frequent use of nail polish and 1.30 (95% CI: 0.85, 1.99) for nail polish remover. In Latinas, any use of artificial nails or fill-ins was associated with BC incidence (HR=2.87; 95% CI: 1.19, 6.91). Among White women, we observed an association with frequent use of perfume (HR=1.17; 95% CI: 1.00, 1.35), but not nail products. Frequent use of pomade was positively associated with BC in Latinas (HR=2.43; 95% CI: 1.27, 4.67) (Table 4). Among Black women, the HR was 1.55 (95% CI: 0.82, 2.96) for frequent pomade use and 1.78 (95% CI: 0.89, 3.53) for some use. Among White women, the HR for frequent pomade use was 1.69 (95% CI: 0.76, 3.75). HRs ranged from 1.13 to 1.26 for body lotions and creams in Black and Latina women and petroleum jelly in Black women, although CIs were wide. Frequent hand lotion use was inversely associated with BC in White women (HR=0.85; 95% CI: 0.74, 0.97) (Table 5). Frequent use of blemish/acne products was associated with BC in White women (HR=1.16; 95% CI: 1.04, 1.29). The inference was similar in models that accounted for coexposure to other correlated products through adjustment for the total number of beauty, hair, or skincare/hygiene products used (Tables S9–S11).

Table 3.

Associations between use of self-reported single beauty products during the 10- to 13-years-of-age period and incident breast cancer by race and ethnicity in the Sister Study.

Product Black or African American (n=4,049) Non-Black Hispanic/Latina (n=2,104) Non-Hispanic White (n=39,312)
Use n cases Adjusted HR (95% CI)a Use n cases Adjusted HR (95% CI)a Use n cases Adjusted HR (95% CI)a
Mascara Frequently or sometimes 13 0.89 (0.51, 1.55) Frequently 5 0.96 (0.39, 2.35) Frequently 109 1.02 (0.84, 1.23)
Sometimes 16 0.83 (0.48, 1.41) Sometimes 447 0.95 (0.86, 1.05)
Did not use 264 1 (Ref) Did not use 107 1 (Ref) Did not use 2,550 1 (Ref)
Eye shadow Frequently or sometimesb 17 1.12 (0.68, 1.85) Frequently or sometimes 20 0.76 (0.46, 1.23) Frequently 62 0.92 (0.71, 1.18)
Sometimes 443 0.99 (0.89, 1.10)
Did not useb 260 1 (Ref) Did not use 108 1 (Ref) Did not use 2,610 1 (Ref)
Eye liner Frequently or sometimes 14 0.91 (0.52, 1.57) Frequently 5 1.31 (0.54, 3.21) Frequently 55 1.22 (0.94, 1.60)
Sometimes 15 1.11 (0.64, 1.92) Sometimes 216 1.01 (0.88, 1.16)
Did not use 262 1 (Ref) Did not use 108 1 (Ref) Did not use 2,833 1 (Ref)
Lipstick Frequently 13 1.91 (1.09, 3.32) Frequently 8 1.26 (0.61, 2.60) Frequently 163 1.22 (1.04, 1.44)
Sometimes 34 0.99 (0.69, 1.42) Sometimes 24 0.88 (0.56, 1.38) Sometimes 886 1.05 (0.97, 1.14)
Did not use 229 1 (Ref) Did not use 96 1 (Ref) Did not use 2,039 1 (Ref)
Lip moisturizer Frequently 31 1.24 (0.83, 1.86) Frequently 7 0.71 (0.33, 1.56) Frequently 305 0.95 (0.83, 1.09)
Sometimes 96 1.05 (0.80, 1.38) Sometimes 43 1.18 (0.81, 1.73) Sometimes 1,302 0.96 (0.88, 1.04)
Did not use 144 1 (Ref) Did not use 75 1 (Ref) Did not use 1,391 1 (Ref)
Foundation Frequently or sometimes 14 1.45 (0.84, 2.50) Frequently or sometimes 15 1.08 (0.63, 1.84) Frequently 47 0.89 (0.67, 1.19)
Sometimes 293 1.08 (0.96, 1.22)
Did not use 262 1 (Ref) Did not use 113 1 (Ref) Did not use 2,758 1 (Ref)
Blush or rouge Frequently or sometimes 17 1.10 (0.67, 1.80) Frequently 6 1.73 (0.73, 4.08) Frequently 71 1.00 (0.78, 1.27)
Sometimes 19 0.81 (0.50, 1.33) Sometimes 526 1.04 (0.95, 1.15)
Did not use 258 1 (Ref) Did not use 103 1 (Ref) Did not use 2,489 1 (Ref)
Makeup remover Frequently or sometimes <5 c NEc Frequently or sometimesb 13 1.41 (0.78, 2.55) Frequently 28 1.60 (1.10, 2.32)
Sometimes 125 1.03 (0.86, 1.23)
Did not use 275 NEc Did not useb 113 1 (Ref) Did not use 2,958 1 (Ref)
Nail polish Frequently 30 1.23 (0.81, 1.86) Frequently 11 1.26 (0.65, 2.44) Frequently 177 0.91 (0.78, 1.07)
Sometimes 138 0.95 (0.73, 1.23) Sometimes 60 1.23 (0.84, 1.80) Sometimes 1,616 0.99 (0.92, 1.06)
Did not use 96 1 (Ref) Did not use 51 1 (Ref) Did not use 1,199 1 (Ref)
Nail polish remover Frequently 27 1.30 (0.85, 1.99) Frequently 9 1.09 (0.53, 2.22) Frequently 142 0.85 (0.72, 1.02)
Sometimes 135 0.98 (0.76, 1.27) Sometimes 61 1.23 (0.84, 1.79) Sometimes 1,569 0.99 (0.91, 1.06)
Did not use 104 1 (Ref) Did not use 53 1 (Ref) Did not use 1,270 1 (Ref)
Cuticle cream Frequentlyb 5 2.87 (1.25, 6.57) Frequently or sometimes 9 0.75 (0.38, 1.49) Frequently 8 0.71 (0.36, 1.42)
Sometimesb 20 0.92 (0.58, 1.47) Sometimes 225 1.04 (0.91, 1.19)
Did not useb 248 1 (Ref) Did not use 115 1 (Ref) Did not use 2,830 1 (Ref)
Artificial nails or fill-ins Frequently or sometimes <5 c NEc Frequently or sometimes 5 2.87 (1.19, 6.91) Frequently or sometimes 19 1.09 (0.69, 1.70)
Did not use 274 NEc Did not use 123 1 (Ref) Did not use 3,109 1 (Ref)
Perfume or cologne Frequently 17 0.85 (0.51, 1.42) Frequently 16 0.97 (0.54, 1.74) Frequently 203 1.17 (1.00, 1.35)
Sometimes 147 1.10 (0.86, 1.42) Sometimes 65 1.21 (0.81, 1.81) Sometimes 1,626 1.06 (0.98, 1.15)
Did not use 106 1 (Ref) Did not use 38 1 (Ref) Did not use 1,159 1 (Ref)

Note: Participants with missing data on the product of interest are excluded from single-product model. CI, confidence interval; HR, hazard ratio; NE, not estimated; Ref, reference.

a

Adjusted for birth cohort in 10-y intervals, family income level growing up (well off, middle income, low income, poor), and maximum household education level at 13 years of age (less than high school, high school graduate or equivalent, some college or technical school, 4-y degree or higher) in addition to age as the timescale.

b

Proportional hazards assumption violated for product use variable (p<0.05).

c

We did not estimate associations for products with <5 exposed cases. To protect participant confidentiality, we do not report exact case numbers if <5.

Table 4.

Associations between self-reported use of single hair products during the 10- to 13-years-of-age period and incident breast cancer by race and ethnicity in the Sister Study.

Product Black or African American (n=4,049) Non-Black Hispanic/Latina (n=2,104) Non-Hispanic White (n=39,312)
Use n cases Adjusted HR (95% CI)a Use n cases Adjusted HR (95% CI)a Use n cases Adjusted HR (95% CI)a
Shampoo Frequentlyb 194 1.44 (0.77, 2.69) Frequently 104 1 (Ref) Frequently 2,756 1.07 (0.71, 1.63)
Sometimesb 64 1.13 (0.59, 2.19) Sometimes 11 0.63 (0.34, 1.19) Sometimes 300 1.07 (0.70, 1.64)
Did not useb 10 1 (Ref) Did not use 6 0.64 (0.27, 1.49) Did not use 23 1 (Ref)
Conditioner or rinse Frequently 74 1.04 (0.74, 1.47) Frequently 53 1.36 (0.84, 2.21) Frequently 920 1.04 (0.94, 1.15)
Sometimes 93 1.29 (0.96, 1.75) Sometimes 33 1.27 (0.77, 2.10) Sometimes 896 1.04 (0.95, 1.15)
Did not use 93 1 (Ref) Did not use 33 1 (Ref) Did not use 1,167 1 (Ref)
Hair spray Frequently or sometimes 49 1.11 (0.81, 1.51) Frequently 6 0.91 (0.38, 2.15) Frequentlyb 260 1.10 (0.97, 1.26)
Sometimes 38 0.99 (0.66, 1.47) Sometimesb 969 1.05 (0.97, 1.14)
Did not use 226 1 (Ref) Did not use 80 1 (Ref) Did not useb 1,784 1 (Ref)
Hair styling gel or mousse Frequently or sometimes 27 0.99 (0.66, 1.49) Frequently or sometimes 15 0.76 (0.44, 1.31) Frequentlyb 79 1.10 (0.87, 1.38)
Sometimesb 371 1.00 (0.90, 1.12)
Did not use 246 1 (Ref) Did not use 113 1 (Ref) Did not useb 2,605 1 (Ref)
Pomade or hair grease Frequently 214 1.55 (0.82, 2.96) Frequently 11 2.43 (1.27, 4.67) Frequently 6 1.69 (0.76, 3.75)
Sometimes 50 1.78 (0.89, 3.53) Sometimes 11 0.79 (0.42, 1.47) Sometimes 52 1.02 (0.77, 1.34)
Did not use 10 1 (Ref) Did not use 103 1 (Ref) Did not use 3,056 1 (Ref)
Hair food Frequently 16 1.19 (0.69, 2.04) Frequently or sometimes 10 0.92 (0.48, 1.77) Frequently or sometimes 9 1.18 (0.61, 2.28)
Sometimes 46 0.93 (0.66, 1.30)
Did not use 207 1 (Ref) Did not use 117 1 (Ref) Did not use 3,082 1 (Ref)

Note: Participants with missing data on the product of interest are excluded from single-product model. CI, confidence interval; HR, hazard ratio; Ref, reference.

a

Adjusted for birth cohort in 10-y intervals, family income level growing up (well off, middle income, low income, poor), and maximum household education level at 13 years of age (less than high school, high school graduate or equivalent, some college or technical school, 4-y degree or higher) in addition to age as the timescale.

b

Proportional hazards assumption violated for product use variable (p<0.05).

Table 5.

Associations between self-reported use of single skincare/hygiene products during the 10- to 13-years-of-age period and incident breast cancer by race and ethnicity in the Sister Study.

Product Black or African American (n=4,049) Non-Black Hispanic/Latina (n=2,104) Non-Hispanic White (n=39,312)
Use n cases Adjusted HR (95% CI)a Use n cases Adjusted HR (95% CI)a Use n cases Adjusted HR (95% CI)a
Body lotions or creams Frequently 157 1.18 (0.80, 1.75) Frequently 28 1.26 (0.78, 2.05) Frequently 250 0.91 (0.79, 1.04)
Sometimes 81 1.26 (0.84, 1.90) Sometimes 41 1.00 (0.65, 1.53) Sometimes 1,305 0.96 (0.89, 1.03)
Did not use 34 1 (Ref) Did not use 53 1 (Ref) Did not use 1,415 1 (Ref)
Hand lotions or creams Frequently 124 1.02 (0.71, 1.48) Frequently 22 0.97 (0.58, 1.63) Frequently 283 0.85 (0.74, 0.97)
Sometimes 105 1.18 (0.81, 1.71) Sometimes 50 1.03 (0.69, 1.54) Sometimes 1,577 0.93 (0.86, 1.01)
Did not use 38 1 (Ref) Did not use 49 1 (Ref) Did not use 1,100 1 (Ref)
Foot lotions or creams Frequently 25 0.96 (0.63, 1.45) Frequently or sometimes 21 1.20 (0.75, 1.92) Frequently 12 0.66 (0.37, 1.15)
Sometimes 35 0.83 (0.58, 1.19) Sometimes 144 0.85 (0.72, 1.00)
Did not use 213 1 (Ref) Did not use 102 1 (Ref) Did not use 2,919 1 (Ref)
Baby oil or mineral-based oils Frequentlyb 55 1.23 (0.88, 1.72) Frequently 7 1.16 (0.52, 2.60) Frequently 172 0.97 (0.83, 1.13)
Sometimesb 113 1.23 (0.94, 1.62) Sometimes 36 0.85 (0.57, 1.27) Sometimes 1,253 0.98 (0.90, 1.05)
Did not useb 101 1 (Ref) Did not use 79 1 (Ref) Did not use 1,589 1 (Ref)
Petroleum jelly Frequently 139 1.13 (0.80, 1.59) Frequently or sometimes 24 0.92 (0.59, 1.43) Frequently 48 0.93 (0.70, 1.24)
Sometimes 94 0.97 (0.68, 1.40) Sometimes 599 0.97 (0.89, 1.06)
Did not use 42 1 (Ref) Did not use 100 1 (Ref) Did not use 2,352 1 (Ref)
Skin lighteners Frequently or sometimes 17 1.20 (0.73, 1.96) Frequently or sometimes <5 c NEc Frequently or sometimes 5 0.97 (0.40, 2.35)
Did not use 261 1 (Ref) Did not use 128 NEc Did not use 3,129 1 (Ref)
Self-tanning products Frequently or sometimes <5 c NEc Frequently or sometimes 6 1.01 (0.45, 2.28) Frequently 9 0.94 (0.49, 1.81)
Sometimes 147 0.93 (0.79, 1.10)
Did not use 276 NEc Did not use 121 1 (Ref) Did not use 2,965 1 (Ref)
Bath or shower gel Frequently 19 1.06 (0.66, 1.70) Frequently or sometimes 8 0.66 (0.32, 1.38) Frequently 44 1.14 (0.85, 1.54)
Sometimes 26 0.99 (0.65, 1.50) Sometimes 121 0.93 (0.77, 1.12)
Did not use 231 1 (Ref) Did not use 115 1 (Ref) Did not use 2,919 1 (Ref)
Shaving cream or gel Frequently or sometimes 20 0.89 (0.56, 1.42) Frequently or sometimes 25 0.96 (0.61, 1.51) Frequently 130 1.13 (0.95, 1.35)
Sometimes 669 1.01 (0.93, 1.11)
Did not use 253 1 (Ref) Did not use 99 1 (Ref) Did not use 2,205 1 (Ref)
Deodorant or antiperspirant Frequently 224 1.45 (0.86, 2.44) Frequently 60 0.89 (0.57, 1.39) Frequently 1,336 1.02 (0.93, 1.12)
Sometimes 31 0.91 (0.49, 1.68) Sometimes 24 0.84 (0.49, 1.44) Sometimes 861 0.95 (0.86, 1.04)
Did not use 16 1 (Ref) Did not use 31 1 (Ref) Did not use 740 1 (Ref)
Face cream or moisturizer Frequently 24 0.94 (0.62, 1.44) Frequently 6 0.67 (0.29, 1.57) Frequentlyb 107 0.95 (0.78, 1.15)
Sometimes 40 0.92 (0.65, 1.29) Sometimes 15 0.95 (0.55, 1.65) Sometimesb 438 1.01 (0.91, 1.12)
Did not use 210 1 (Ref) Did not use 106 1 (Ref) Did not useb 2,522 1 (Ref)
Cleansing cream Frequently 8 0.59 (0.29, 1.20) Frequently 5 0.84 (0.34, 2.10) Frequently 117 0.96 (0.79, 1.15)
Sometimes 23 0.61 (0.40, 0.95) Sometimes 17 0.95 (0.57, 1.59) Sometimes 456 1.04 (0.94, 1.15)
Did not use 245 1 (Ref) Did not use 105 1 (Ref) Did not use 2,498 1 (Ref)
Face masks Frequently or sometimes 13 1.25 (0.71, 2.21) Frequently or sometimes 12 1.15 (0.62, 2.15) Frequently or sometimes 190 1.13 (0.97, 1.31)
Did not use 265 1 (Ref) Did not use 115 1 (Ref) Did not use 2,927 1 (Ref)
Blemish or acne products Frequently 20 1.15 (0.73, 1.81) Frequently 8 0.72 (0.34, 1.51) Frequently 473 1.16 (1.04, 1.29)
Sometimes 60 1.03 (0.77, 1.38) Sometimes 33 0.97 (0.64, 1.48) Sometimes 1,094 1.07 (0.98, 1.16)
Did not use 196 1 (Ref) Did not use 85 1 (Ref) Did not use 1,500 1 (Ref)
Mouthwash or rinse Frequently 71 1.13 (0.83, 1.55) Frequently 7 0.65 (0.30, 1.40) Frequently 129 1.08 (0.90, 1.29)
Sometimes 100 1.00 (0.76, 1.33) Sometimes 32 0.92 (0.61, 1.40) Sometimes 762 0.95 (0.88, 1.04)
Did not use 99 1 (Ref) Did not use 77 1 (Ref) Did not use 2,065 1 (Ref)
Talcum powder under arms Frequently 24 1.14 (0.74, 1.75) Frequently 6 1.03 (0.44, 2.42) Frequently 89 0.96 (0.78, 1.19)
Sometimes 93 1.05 (0.81, 1.36) Sometimes 27 0.89 (0.58, 1.39) Sometimes 609 0.93 (0.85, 1.02)
Did not use 149 1 (Ref) Did not use 89 1 (Ref) Did not use 2,239 1 (Ref)
Talcum powder on genital area Frequently 25 1.13 (0.74, 1.73) Frequently or sometimes 16 0.79 (0.47, 1.32) Frequently 73 1.01 (0.80, 1.27)
Sometimes 72 0.91 (0.69, 1.19) Sometimes 429 0.92 (0.83, 1.02)
Did not use 177 1 (Ref) Did not use 111 1 (Ref) Did not use 2,511 1 (Ref)
Talcum powder on other areas Frequently 36 0.96 (0.66, 1.40) Frequently 7 0.80 (0.37, 1.73) Frequently 121 0.94 (0.78, 1.12)
Sometimes 127 1.00 (0.77, 1.30) Sometimes 41 0.85 (0.58, 1.26) Sometimes 1,074 0.92 (0.85, 0.99)
Did not use 105 1 (Ref) Did not use 69 1 (Ref) Did not use 1,717 1 (Ref)

Note: Participants with missing data on the product of interest are excluded from single-product model. CI, confidence interval; HR, hazard ratio; NE, not estimated; Ref, reference.

a

Adjusted for birth cohort in 10-y intervals, family income level growing up (well off, middle income, low income, poor), and maximum household education level at 13 years of age (less than high school, high school graduate or equivalent, some college or technical school, 4-y degree or higher) in addition to age as the timescale.

b

Proportional hazards assumption violated for product use variable (p<0.05).

c

We did not estimate associations for products with <5 exposed cases. To protect participant confidentiality, we do not report exact case numbers if <5.

Sensitivity Analyses for Hair Product Models, Excluding Straightener/Relaxer Users

Approximately 75% of Black, 8.5% of Latina, and 3.5% of White women reported straightener/relaxer use during the 10- to 13-years-of-age period. Use of straighteners/relaxers was correlated with pomade use among Black and Latina women (rho=0.3), but not White women (rho=0.1). Among Black nonstraightener/relaxer users (n=980), the HR for BC associated with the frequent shampoo, conditioner, and pomade use and some hair spray, hair gel, and hair food use class was farther from the null but imprecise (HR=1.62; 95% CI: 0.85, 3.10), whereas the HR for frequent use of shampoo, conditioner, and pomade was 1 (95% CI: 0.59, 1.71). HRs of hair product classes with incident BC were slightly attenuated among Latina nonstraightener/relaxer users [n=1,888, HR=1.21 (95% CI: 0.67, 2.20) for frequent shampoo and conditioner and some hair spray, hair food, hair gel, and pomade use and HR=1.53 (95% CI: 0.90, 2.60) for frequent shampoo and conditioner use]. The HRs for BC associated with pomade use restricted to nonstraightener/relaxer users were stronger in magnitude in Black women [HR=1.75 (95% CI: 0.72, 4.26) for frequent and HR=1.91 (95% CI: 0.74, 4.96) for some pomade use vs. did not use] and slightly attenuated in Latina and White women [HR=1.28 (95% CI: 0.45, 3.68) and HR=1.41 (95% CI: 0.53, 3.76) for frequent use, respectively] compared with our overall results.

Sensitivity Analyses Excluding Bi- or Multiracial Black Women and Black Latinas

Associations of latent classes of product use with incident BC and results from single-product models were similar in analyses excluding bi- or multiracial Black women and Black Latinas (Table S12). Frequent use of foundation was also associated with BC risk in analyses excluding bi- or multiracial Black women and Black Latinas (HR=1.85; 95% CI: 1.07, 3.17).

Discussion

In this US-wide prospective cohort, we characterized patterns of PCP use during the 10- to 13-years-of-age period among Black, Latina, and White women through latent class analyses and examined associations of product use classes and individual product use with BC incidence. There were clear differences in product use by race and ethnicity, particularly for hair pomade, body moisturizers, and some hygiene products, which were used much more frequently by Black participants. Classes of PCP use during puberty were not clearly associated with BC incidence. Although CIs were wide, point estimates suggested a possible higher hazard of BC associated with latent classes characterized by greater use of nail and hair products among Black and Latina women, whereas point estimates for all beauty and hair product classes were close to the null among White women. Associations of classes of skincare/hygiene product use with BC incidence varied by race and ethnicity, with no clear trends observed. In single-product models, lipstick, makeup remover, nail products, perfume, pomade, and blemish/acne product use were positively associated with BC incidence in at least one racial and ethnic group, and hand cream was inversely associated with BC in White women only.

Classes characterized by use of makeup products were not associated with risk. However, use of makeup remover, which may serve as a surrogate for greater makeup use, was positively associated with BC incidence in White women. We observed positive associations of lipstick use with BC in Black, White, and possibly Latina women. Lipstick may be reapplied throughout the day and women may be exposed to the chemicals in lipsticks through ingestion in addition to dermal absorption, leading to greater chemical exposure. Lip moisturizers were not associated with BC, suggesting that the types of chemicals or chemical concentrations within lipstick products specifically may be associated with increased risk. Lipsticks have been found to contain EDCs, such as phthalates, parabens, and alkylphenols,1,4 as well as metals, including lead.49

Latent class models suggested that frequent use of nail products may be positively associated with BC among Black and Latina women, with stronger HRs observed when restricted to invasive disease. Single-product models also supported an association with nail products. Nail products have been found to contain plasticizers, including phthalates and organophosphates,1,50 metals,51 and other toxic chemicals known or suspected to be carcinogenic,52 such as formaldehyde, toluene, benzene, and methylene chloride.50,5355 In White women, frequent use of perfume, a source of exposure to phthalates, musk, and other fragrances,4 was associated with incident BC. Thousands of chemicals can be used as fragrances in cosmetics, and fragrance components do not have to be listed in product ingredients.56 Women of different racial and ethnic backgrounds may choose different product types and brands,3 and the chemical composition of products may vary depending on whether they are targeted to minoritized groups vs. White women,34 which may contribute to differences in the BC associations for specific product types by race and ethnicity.

Latent classes representing greater hair product use, characterized based on higher frequency of use of more types of products, were suggestively associated with BC in Black and Latina women. Single-product models suggested that pomade use, which is strongly patterned by race, may be associated with higher risk. Hair pomades are leave-in maintenance products used to smooth, moisturize, and style hair and may be water-, oil- or wax-based.48 In general, leave-in products have been found to have higher concentrations of some chemicals, including phthalates and parabens, than rinse-off products1 and remain on the hair or scalp until the next shampoo, which may result in greater absorption.37,57 Our questionnaire did not distinguish between rinse-off and leave-in conditioner and did not include use of other hair products, such as hair oils and lotions, which are used more frequently by Black and Latina women37 and have been linked to reproductive and endocrine-sensitive outcomes.5860 Use of other hair products by pomade users may contribute to the associations we observed.

Previous studies of hair and skincare products that are popular among Black women found that most contained EDCs34 and demonstrated either estrogenic or anti-estrogenic activity in vitro.61,62 Petroleum jelly (petrolatum), frequently used by Black women in our cohort as a skin moisturizer and also an ingredient in some pomades,48 exhibited estrogenic activity61 and can be contaminated by polycyclic aromatic hydrocarbons,56 endocrine-disrupting and carcinogenic compounds that are associated with BC risk.5 The estrogenic or anti-estrogenic activity of each product was not predictable based on their ingredients, suggesting the importance of product-specific chemical mixtures.61 Differences in the chemical constituents and hormonal activity within the same types of skincare products (e.g., cocoa butter cream was anti-estrogenic, whereas other lotions were estrogenic61) may explain why there were no clear trends overall for skincare/hygiene products with BC incidence and some differences by race and ethnicity. Among Black women, HRs suggested a possible modest increase in risk associated with the latent class characterized by frequent lotion and moisturizer use and for single-product models of these commonly used products (body lotions, body oils, and petroleum jelly).

Previous analyses in the Sister Study have observed higher BC risk associated with greater beauty product use in the 12 months before enrollment, assessed first using latent class-based groupings of adult product use18 and more recently using quantile-based g-computation to estimate joint effects of use of multiple products.20 Associations with adult use were observed in White but not Black women,18,20 and adult use of lipstick, nail products, and perfume were not associated with BC in single-product models in the full cohort.20 Latent classes of hair product use in the year before enrollment were not associated with BC incidence in Black or White women.18 These inconsistencies with our findings for adolescent use suggest that use of beauty and hair products during puberty may influence BC risk independent of use later in life, but we did not conduct mediation analyses to quantify the direct effects of PCP use during puberty on BC incidence after accounting for the potential pathway through adult use. Changes in chemical composition of products over time or differences in products used in adolescence vs. adulthood could contribute to differences in risk by age at use. Patterns of adult product use in Black women also may not have been well characterized in the prior LCA, which was not stratified by race.

Previous studies of adult use of skincare/hygiene products and BC risk have yielded inconsistent findings, including within the Sister Study.18,20 Use of hand and facial cream and skin lotion was not associated with BC incidence in a Norwegian cohort.19 Skin lighteners were not associated with BC risk in Ghanaian women,27 which is in line with our null results for adolescent use in Black women. Deodorant/antiperspirant use in adulthood has not been found to be associated with BC risk,21 consistent with our findings for adolescent use. We observed a positive association of use of blemish/acne products with BC in White women. This is consistent with a previous Sister Study finding that severe acne in adolescence, a potential marker of higher endogenous hormone concentrations during puberty, was associated with increased BC risk.63

PCPs contain complex mixtures of biologically active chemicals with potential endocrine-disrupting, genotoxic, and carcinogenic effects that may influence BC risk.5,56 Animal studies support that exposure to environmental chemicals during puberty, a vulnerable window for carcinogenesis owing to the rapid proliferation of breast cells that are not fully differentiated,5,6,22 can disrupt mammary gland development and influence cancer risk.5,7,10,64 Few studies have examined environmental exposures specifically during puberty and BC risk in women.5,22 A recent analysis in the Life Span Study of atomic bomb survivors found that BC risk associated with ionizing radiation exposure increased as the age at exposure approached menarche, was at its peak in women exposed around the time of menarche, and then declined.65 In the Child Health and Development Studies, women exposed to DDT after infancy through puberty (3–13 years of age) were at increased risk of BC at <50 and at 50–54 years of age.66 Our findings in the Sister Study linking use of some PCPs during the 10- to 13-years-of-age period with increased BC risk, in addition to prior work on straightener/relaxer use,26 add to this evidence base supporting that environmental exposures around the time of puberty influence BC risk.

We asked about product use during the 10- to 13-years-of-age period as a proxy for the pubertal period, but this age range does not directly correspond to the timing of puberty in individual participants. More than 80% of participants reported experiencing thelarche, usually the first physical sign of pubertal onset,67 by 14 years of age. We hypothesized that women with early thelarche, who on average experience a longer duration of development than women with later thelarche,68 would be more vulnerable to the effects of EDCs during this critical window. Contrary to that hypothesis, among White women, point estimates for classes characterized by greater product use were positive (although imprecise) only among girls with late thelarche. A possible explanation is that the breast may be more vulnerable to the influence of exogenous estrogens found in products when endogenous hormone levels are low, as in prepubertal girls.61 Because product use often increases during puberty, it is also possible that women with late thelarche who reported more frequent PCP use during the 10- to 13-years-of-age period misreported their age at thelarche as occurring after 13 years of age when it really happened earlier. If this is the case, the elevated HRs for more frequent product use in this group may reflect the increased BC risk associated with earlier age at thelarche that we previously observed in the cohort.42

PCP use in childhood could influence BC risk by affecting the timing of puberty.37 Childhood use of some hair products has been associated with premature breast development69 and earlier menarche58 in Black girls, but findings from epidemiological studies of PCP-related EDC biomarker concentrations and pubertal timing are inconsistent overall.70 We did not have data on PCP use prior to 10 years of age so we could not examine whether childhood PCP use influences BC incidence through altered timing of thelarche or menarche.

The use of the large and diverse Sister Study cohort is a strength of this analysis, allowing us to account for racial and ethnic differences in product use. Even so, the smaller sample sizes for Black and Latina women affected the precision of the effect estimates and limited our ability to stratify or detect statistical heterogeneity. For example, we lacked sufficient cases of premenopausal and ER-negative cancers to evaluate whether PCP use during puberty contributes to disparate risks of these more aggressive cancers in Black and Latina women.7173 We also could not stratify by timing of thelarche in Black or Latina women, who are at increased risk of early thelarche compared with White women.74

We classified women into broad categories based on self-reported race and ethnicity that are only a crude proxy for lived experiences of structural racism and discrimination. We did not examine women who self-identified as Black and at least one other race or as Black and Latina separately from women who self-identified as Black only owing to small numbers (n=352). Because the number of non-Black Latina participants was relatively small (n=2,104), we did not disaggregate by subpopulation based on origin or culture or consider race within this group. Prior studies observed distinct patterns of PCP use among Asian women compared with other races and ethnicities,29,31 but we had too few women who self-identified as Asian, Pacific Islanders, American Indians, or Alaska natives to examine these groups. We did not account for intersectionality of other identities (e.g., gender identity, sexual orientation, SES) that influence lived experiences and, potentially, PCP use.32,33,75 Our results could also be subject to residual confounding by other sources of chemical exposures during childhood, such as food packaging, use of other consumer products, and ambient environmental exposures. The Sister Study is a relatively high-SES, volunteer cohort and all participants have a family history of BC, which may limit the generalizability of our findings to the broader population. However, estimated associations are internally valid and an advantage of the family-based design is the enhanced ability to detect effects of environmental exposures that interact with genetic factors.76,77 Sisters also likely share lifestyles and early life exposures, so sisters of women with BC may be more likely to have early life exposures related to increased BC risk,76 improving our ability to detect these associations.

A strength of this analysis is the use of latent class models to identify groups of women with similar product use patterns, which reduced the dimensionality of the correlated, single-product data and characterized patterns of joint product use that occur in real-life settings.78 We did not account for uncertainty in probability-based latent class assignment in our BC models, which can produce a bias toward the null.46,79 A limitation of the latent class approach, which is agnostic to the outcome of interest, is that it may obscure associations of specific products with BC risk. Products differ in terms of the types of chemicals or concentrations of chemicals included4 and may differentially influence susceptibility to breast carcinogenesis. Frequency of exposure could also vary across products included in a particular latent class. For example, the latent class analyses of beauty products grouped “frequent” and “sometimes” users of makeup products into the same identified class. Thus, our single-product analyses are an important addition and identified specific products that may warrant additional research, despite the possibility of false-positive findings due to multiple testing. Single-product analyses also provide context relevant to the interpretation of the latent class findings by singling out products that may be driving class-level associations. We did not adjust for multiple comparisons because the trade-off of decreasing the likelihood of false-positive findings is an increase in the likelihood of false-negative findings.80,81 However, results from single-product models should be interpreted with caution, and subsequent studies are needed to confirm our findings.

Participants recalled their product use during the 10- to 13-years-of-age period at baseline, which was anywhere from 25 to 64 y later, depending on age at enrollment. The validity of this recalled data is not known, an important limitation of this work. We recently reported that Sister Study participants can generally recall lifetime use of feminine hygiene products with good consistency across two time points,82 although the reliability of use during the 10- to 13-years-of-age period specifically could not be estimated owing to differences in the ages when use was assessed on the enrollment and follow-up questionnaire. We asked about adolescent product use using broad categories, which may have minimized misclassification, but the response options of “sometimes” and “frequently” were subject to participants’ interpretation. Owing to the prospective study design, we expect exposure misclassification to be nondifferential by BC status, resulting in a potential underestimation of associations of frequent use with BC risk. We did not have information on the specific products/brands used and could not evaluate the constituent chemicals that women were exposed to. The chemical formulations of products on the market when the participants were 10–13 years of age may have changed across the birth cohorts included in our study and likely differ from products available today. Some changes to product formulations have been prompted by consumer concerns regarding chemical exposures,83,84 so our results may not be generalizable to BC risk associated with PCP use among current adolescents.

In conclusion, our findings provide some support for the hypothesis that frequent use of some PCPs during puberty is associated with increased BC risk. Additional research is needed to corroborate our findings, examine adolescent use of products currently on the market and the chemical constituents within these products that contribute to increased risk, and consider how differences in early life PCP use by race and ethnicity contribute to BC disparities. PCP use is a potentially modifiable source of exposure to EDCs that is amenable to multiple levels of intervention, including changes to individual product use,85 product formulations,84 and policy or product regulations.86,87 More research is needed to further investigate whether reducing PCP use around puberty could provide an opportunity for BC risk reduction starting early in life.

Supplementary Material

Acknowledgments

Funding: This work was supported by the Intramural Research Program of the National Institutes of Health, National Institute of Environmental Health Sciences (NIEHS; Z01-ES044005 to D.P.S.).

Data sharing: Requests for data, including the data used in this manuscript, are welcome. De-identified data is made available upon request as described on the study website (https://sisterstudy.niehs.nih.gov/English/data-requests.htm). The data sharing policy was developed to protect the privacy of study participants and is consistent with study informed consent documents as approved by the NIEHS institutional review board.

Conclusions and opinions are those of the individual authors and do not necessarily reflect the policies or views of EHP Publishing or the National Institute of Environmental Health Sciences.

References

  • 1.Guo Y, Kannan K. 2013. A survey of phthalates and parabens in personal care products from the United States and its implications for human exposure. Environ Sci Technol 47(24):14442–14449, PMID: , 10.1021/es4042034. [DOI] [PubMed] [Google Scholar]
  • 2.Gao CJ, Kannan K. 2020. Phthalates, bisphenols, parabens, and triclocarban in feminine hygiene products from the United States and their implications for human exposure. Environ Int 136:105465, PMID: , 10.1016/j.envint.2020.105465. [DOI] [PubMed] [Google Scholar]
  • 3.Johnson PI, Favela K, Jarin J, Le AM, Clark PY, Fu L, et al. 2022. Chemicals of concern in personal care products used by women of color in three communities of California. J Expo Sci Environ Epidemiol 32(6):864–876, PMID: , 10.1038/s41370-022-00485-y. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 4.Dodson RE, Nishioka M, Standley LJ, Perovich LJ, Brody JG, Rudel RA. 2012. Endocrine disruptors and asthma-associated chemicals in consumer products. Environ Health Perspect 120(7):935–943, PMID: , 10.1289/ehp.1104052. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 5.Rodgers KM, Udesky JO, Rudel RA, Brody JG. 2018. Environmental chemicals and breast cancer: an updated review of epidemiological literature informed by biological mechanisms. Environ Res 160:152–182, PMID: , 10.1016/j.envres.2017.08.045. [DOI] [PubMed] [Google Scholar]
  • 6.Rudel RA, Fenton SE, Ackerman JM, Euling SY, Makris SL. 2011. Environmental exposures and mammary gland development: state of the science, public health implications, and research recommendations. Environ Health Perspect 119(8):1053–1061, PMID: , 10.1289/ehp.1002864. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 7.Kay JE, Cardona B, Rudel RA, Vandenberg LN, Soto AM, Christiansen S, et al. 2022. Chemical effects on breast development, function, and cancer risk: existing knowledge and new opportunities. Curr Environ Health Rep 9(4):535–562, PMID: , 10.1007/s40572-022-00376-2. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 8.Braun JM, Just AC, Williams PL, Smith KW, Calafat AM, Hauser R. 2014. Personal care product use and urinary phthalate metabolite and paraben concentrations during pregnancy among women from a fertility clinic. J Expo Sci Environ Epidemiol 24(5):459–466, PMID: , 10.1038/jes.2013.69. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 9.Darbre PD. 2021. Endocrine disrupting chemicals and breast cancer cells. Adv Pharmacol 92:485–520, PMID: , 10.1016/bs.apha.2021.04.006. [DOI] [PubMed] [Google Scholar]
  • 10.Macon MB, Fenton SE. 2013. Endocrine disruptors and the breast: early life effects and later life disease. J Mammary Gland Biol Neoplasia 18(1):43–61, PMID: , 10.1007/s10911-013-9275-7. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 11.López-Carrillo L, Hernández-Ramírez RU, Calafat AM, Torres-Sánchez L, Galván-Portillo M, Needham LL, et al. 2010. Exposure to phthalates and breast cancer risk in northern Mexico. Environ Health Perspect 118(4):539–544, PMID: , 10.1289/ehp.0901091. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 12.Reeves KW, Díaz Santana M, Manson JE, Hankinson SE, Zoeller RT, Bigelow C, et al. 2019. Urinary phthalate biomarker concentrations and postmenopausal breast cancer risk. J Natl Cancer Inst 111(10):1059–1067, PMID: , 10.1093/jnci/djz002. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 13.Parada H Jr, Gammon MD, Chen J, Calafat AM, Neugut AI, Santella RM, et al. 2018. Urinary phthalate metabolite concentrations and breast cancer incidence and survival following breast cancer: the Long Island Breast Cancer Study Project. Environ Health Perspect 126(4):047013, PMID: , 10.1289/EHP2083. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 14.Parada H Jr, Gammon MD, Ettore HL, Chen J, Calafat AM, Neugut AI, et al. 2019. Urinary concentrations of environmental phenols and their associations with breast cancer incidence and mortality following breast cancer. Environ Int 130:104890, PMID: , 10.1016/j.envint.2019.05.084. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 15.Zhang X, Wolff MS, Shen J, Parada H Jr, Santella RM, Neugut AI, et al. 2022. Phthalates and phenols, leukocyte telomere length, and breast cancer risk and mortality in the Long Island Breast Cancer Study Project. Cancer Epidemiol Biomarkers Prev 31(1):117–123, PMID: , 10.1158/1055-9965.EPI-21-0830. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 16.Wu AH, Franke AA, Wilkens LR, Tseng C, Conroy SM, Li Y, et al. 2021. Urinary phthalate exposures and risk of breast cancer: the Multiethnic Cohort study. Breast Cancer Res 23(1):44, PMID: , 10.1186/s13058-021-01419-6. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 17.Wu AH, Franke AA, Wilkens LR, Tseng C, Conroy SM, Li Y, et al. 2021. Risk of breast cancer and prediagnostic urinary excretion of bisphenol A, triclosan and parabens: the Multiethnic Cohort study. Int J Cancer 149(7):1426–1434, PMID: , 10.1002/ijc.33692. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 18.Taylor KW, Troester MA, Herring AH, Engel LS, Nichols HB, Sandler DP, et al. 2018. Associations between personal care product use patterns and breast cancer risk among White and Black women in the Sister Study. Environ Health Perspect 126(2):027011, PMID: , 10.1289/EHP1480. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 19.Rylander C, Veierød MB, Weiderpass E, Lund E, Sandanger TM. 2019. Use of skincare products and risk of cancer of the breast and endometrium: a prospective cohort study. Environ Health 18(1):105, PMID: , 10.1186/s12940-019-0547-6. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 20.Chang CJ, O’Brien KM, Keil AP, Goldberg M, Taylor KW, Sandler DP, et al. 2023. Use of personal care product mixtures and incident hormone-sensitive cancers in the Sister Study: a U.S.-wide prospective cohort. Environ Int 183:108298, PMID: , 10.1016/j.envint.2023.108298. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 21.Hardefeldt PJ, Edirimanne S, Eslick GD. 2013. Deodorant use and breast cancer risk. Epidemiology 24(1):172, PMID: , 10.1097/EDE.0b013e3182781684. [DOI] [PubMed] [Google Scholar]
  • 22.Terry MB, Michels KB, Brody JG, Byrne C, Chen S, Jerry DJ, et al. 2019. Environmental exposures during windows of susceptibility for breast cancer: a framework for prevention research. Breast Cancer Res 21(1):96, PMID: , 10.1186/s13058-019-1168-2. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 23.Martinson HA, Lyons TR, Giles ED, Borges VF, Schedin P. 2013. Developmental windows of breast cancer risk provide opportunities for targeted chemoprevention. Exp Cell Res 319(11):1671–1678, PMID: , 10.1016/j.yexcr.2013.04.018. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 24.Berger KP, Kogut KR, Bradman A, She J, Gavin Q, Zahedi R, et al. 2019. Personal care product use as a predictor of urinary concentrations of certain phthalates, parabens, and phenols in the HERMOSA study. J Expo Sci Environ Epidemiol 29(1):21–32, PMID: , 10.1038/s41370-017-0003-z. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 25.Environmental Working Group. 2008. Teen girls’ body burden of hormone-altering cosmetics chemicals. Updated 24 September 2023. https://www.ewg.org/research/teen-girls-body-burden-hormone-altering-cosmetics-chemicals [accessed 25 April 2023].
  • 26.White AJ, Gregoire AM, Taylor KW, Eberle C, Gaston S, O’Brien KM, et al. 2021. Adolescent use of hair dyes, straighteners and perms in relation to breast cancer risk. Int J Cancer 148(9):2255–2263, PMID: , 10.1002/ijc.33413. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 27.Brinton LA, Figueroa JD, Ansong D, Nyarko KM, Wiafe S, Yarney J, et al. 2018. Skin lighteners and hair relaxers as risk factors for breast cancer: results from the Ghana breast health study. Carcinogenesis 39(4):571–579, PMID: , 10.1093/carcin/bgy002. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 28.Llanos AAM, Rabkin A, Bandera EV, Zirpoli G, Gonzalez BD, Xing CY, et al. 2017. Hair product use and breast cancer risk among African American and White women. Carcinogenesis 38(9):883–892, PMID: , 10.1093/carcin/bgx060. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 29.Dodson RE, Cardona B, Zota AR, Robinson Flint J, Navarro S, Shamasunder B. 2021. Personal care product use among diverse women in California: Taking Stock Study. J Expo Sci Environ Epidemiol 31(3):487–502, PMID: , 10.1038/s41370-021-00327-3. [DOI] [PubMed] [Google Scholar]
  • 30.Wu XM, Bennett DH, Ritz B, Cassady DL, Lee K, Hertz-Picciotto I. 2010. Usage pattern of personal care products in California households. Food Chem Toxicol 48(11):3109–3119, PMID: , 10.1016/j.fct.2010.08.004. [DOI] [PubMed] [Google Scholar]
  • 31.Collins HN, Johnson PI, Calderon NM, Clark PY, Gillis AD, Le AM, et al. 2023. Differences in personal care product use by race/ethnicity among women in California: implications for chemical exposures. J Expo Sci Environ Epidemiol 33(2):292–300, PMID: , 10.1038/s41370-021-00404-7. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 32.Zota AR, Shamasunder B. 2017. The environmental injustice of beauty: framing chemical exposures from beauty products as a health disparities concern. Am J Obstet Gynecol 217(4):418.e1–418.e6, PMID: , 10.1016/j.ajog.2017.07.020. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 33.McDonald JA, Llanos AAM, Morton T, Zota AR. 2022. The environmental injustice of beauty products: toward clean and equitable beauty. Am J Public Health 112(1):50–53, PMID: , 10.2105/AJPH.2021.306606. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 34.Helm JS, Nishioka M, Brody JG, Rudel RA, Dodson RE. 2018. Measurement of endocrine disrupting and asthma-associated chemicals in hair products used by Black women. Environ Res 165:448–458, PMID: , 10.1016/j.envres.2018.03.030. [DOI] [PubMed] [Google Scholar]
  • 35.Nguyen VK, Kahana A, Heidt J, Polemi K, Kvasnicka J, Jolliet O, et al. 2020. A comprehensive analysis of racial disparities in chemical biomarker concentrations in United States women, 1999–2014. Environ Int 137:105496, PMID: , 10.1016/j.envint.2020.105496. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 36.Calafat AM, Ye X, Wong LY, Bishop AM, Needham LL. 2010. Urinary concentrations of four parabens in the U.S. population: NHANES 2005–2006. Environ Health Perspect 118(5):679–685, PMID: , 10.1289/ehp.0901560. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 37.James-Todd T, Senie R, Terry MB. 2012. Racial/ethnic differences in hormonally-active hair product use: a plausible risk factor for health disparities. J Immigr Minor Health 14(3):506–511, PMID: , 10.1007/s10903-011-9482-5. [DOI] [PubMed] [Google Scholar]
  • 38.Santaliz Casiano A, Lee A, Teteh D, Madak Erdogan Z, Treviño L. 2022. Endocrine-disrupting chemicals and breast cancer: disparities in exposure and importance of research inclusivity. Endocrinology 163(5):bqac034, PMID: , 10.1210/endocr/bqac034. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 39.Donovan M, Tiwary CM, Axelrod D, Sasco AJ, Jones L, Hajek R, et al. 2007. Personal care products that contain estrogens or xenoestrogens may increase breast cancer risk. Med Hypotheses 68(4):756–766, PMID: , 10.1016/j.mehy.2006.09.039. [DOI] [PubMed] [Google Scholar]
  • 40.Philippat C, Bennett D, Calafat AM, Picciotto IH. 2015. Exposure to select phthalates and phenols through use of personal care products among Californian adults and their children. Environ Res 140:369–376, PMID: , 10.1016/j.envres.2015.04.009. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 41.Sandler DP, Hodgson ME, Deming-Halverson SL, Juras PS, D’Aloisio AA, Suarez LM, et al. 2017. The Sister Study cohort: baseline methods and participant characteristics. Environ Health Perspect 125(12):127003, PMID: , 10.1289/EHP1923. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 42.Goldberg M, D’Aloisio AA, O’Brien KM, Zhao S, Sandler DP. 2020. Pubertal timing and breast cancer risk in the Sister Study cohort. Breast Cancer Res 22(1):112, PMID: , 10.1186/s13058-020-01326-2. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 43.D’Aloisio AA, Nichols HB, Hodgson ME, Deming-Halverson SL, Sandler DP. 2017. Validity of self-reported breast cancer characteristics in a nationwide cohort of women with a family history of breast cancer. BMC Cancer 17(1):692, PMID: , 10.1186/s12885-017-3686-6. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 44.Lanza ST, Collins LM, Lemmon DR, Schafer JL. 2007. PROC LCA: a SAS procedure for latent class analysis. Struct Equ Modeling 14(4):671–694, PMID: , 10.1080/10705510701575602. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 45.Weller BE, Bowen NK, Faubert SJ. 2020. Latent class analysis: a guide to best practice. J Black Psychol 46(4):287–311, 10.1177/0095798420930932. [DOI] [Google Scholar]
  • 46.Bray BC, Lanza ST, Tan X. 2015. Eliminating bias in classify-analyze approaches for latent class analysis. Struct Equ Modeling 22(1):1–11, PMID: , 10.1080/10705511.2014.935265. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 47.Xue X, Kim MY, Gaudet MM, Park Y, Heo M, Hollenbeck AR, et al. 2013. A comparison of the polytomous logistic regression and joint Cox proportional hazards models for evaluating multiple disease subtypes in prospective cohort studies. Cancer Epidemiol Biomarkers Prev 22(2):275–285, PMID: , 10.1158/1055-9965.EPI-12-1050. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 48.McMichael AJ. 2003. Ethnic hair update: past and present. J Am Acad Dermatol 48(suppl 6):S127–S133, PMID: , 10.1067/mjd.2003.278. [DOI] [PubMed] [Google Scholar]
  • 49.Liu S, Hammond SK, Rojas-Cheatham A. 2013. Concentrations and potential health risks of metals in lip products. Environ Health Perspect 121(6):705–710, PMID: , 10.1289/ehp.1205518. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 50.Young AS, Allen JG, Kim UJ, Seller S, Webster TF, Kannan K, et al. 2018. Phthalate and organophosphate plasticizers in nail polish: evaluation of labels and ingredients. Environ Sci Technol 52(21):12841–12850, PMID: , 10.1021/acs.est.8b04495. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 51.Ceballos DM, Young AS, Allen JG, Specht AJ, Nguyen VT, Craig JA, et al. 2021. Exposures in nail salons to trace elements in nail polish from impurities or pigment ingredients—a pilot study. Int J Hyg Environ Health 232:113687, PMID: , 10.1016/j.ijheh.2020.113687. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 52.NTP (National Toxicology Program). 2021. Report on Carcinogens, Fifteenth Edition. http://ntp.niehs.nih.gov/go/roc15 [accessed 23 May 2023].
  • 53.Voller LM, Persson L, Bruze M, Ericson ME, Hylwa SA. 2019. Formaldehyde in “nontoxic” nail polish. Dermatitis 30(4):259–263, PMID: , 10.1097/DER.0000000000000493. [DOI] [PubMed] [Google Scholar]
  • 54.Quach T, Nguyen KD, Doan-Billings PA, Okahara L, Fan C, Reynolds P. 2008. A preliminary survey of Vietnamese nail salon workers in Alameda County, California. J Community Health 33(5):336–343, PMID: , 10.1007/s10900-008-9107-7. [DOI] [PubMed] [Google Scholar]
  • 55.FDA (U.S. Food and Drug Administration). 2022. Nail Care Products. Updated 25 February 2022. https://www.fda.gov/cosmetics/cosmetic-products/nail-care-products#ingred [accessed 28 November 2023].
  • 56.Chow ET, Mahalingaiah S. 2016. Cosmetics use and age at menopause: is there a connection? Fertil Steril 106(4):978–990, PMID: , 10.1016/j.fertnstert.2016.08.020. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 57.Gaston SA, James-Todd T, Harmon Q, Taylor KW, Baird D, Jackson CL. 2020. Chemical/straightening and other hair product usage during childhood, adolescence, and adulthood among African-American women: potential implications for health. J Expo Sci Environ Epidemiol 30(1):86–96, PMID: , 10.1038/s41370-019-0186-6. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 58.James-Todd T, Terry MB, Rich-Edwards J, Deierlein A, Senie R. 2011. Childhood hair product use and earlier age at menarche in a racially diverse study population: a pilot study. Ann Epidemiol 21(6):461–465, PMID: , 10.1016/j.annepidem.2011.01.009. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 59.Preston EV, Fruh V, Quinn MR, Hacker MR, Wylie BJ, O’Brien K, et al. 2021. Endocrine disrupting chemical-associated hair product use during pregnancy and gestational age at delivery: a pilot study. Environ Health 20(1):86, PMID: , 10.1186/s12940-021-00772-5. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 60.Chan M, Preston EV, Fruh V, Quinn MR, Hacker MR, Wylie BJ, et al. 2023. Use of personal care products during pregnancy and birth outcomes—a pilot study. Environ Res 225:115583, PMID: , 10.1016/j.envres.2023.115583. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 61.Myers SL, Yang CZ, Bittner GD, Witt KL, Tice RR, Baird DD. 2015. Estrogenic and anti-estrogenic activity of off-the-shelf hair and skin care products. J Expo Sci Environ Epidemiol 25(3):271–277, PMID: , 10.1038/jes.2014.32. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 62.James-Todd T, Connolly L, Preston EV, Quinn MR, Plotan M, Xie Y, et al. 2021. Hormonal activity in commonly used Black hair care products: evaluating hormone disruption as a plausible contribution to health disparities. J Expo Sci Environ Epidemiol 31(3):476–486, PMID: , 10.1038/s41370-021-00335-3. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 63.Murphy JD, Sandler D, White AJ, O’Brien KM. 2019. Severe acne and risk of breast cancer. Breast Cancer Res Treat 177(2):487–495, PMID: , 10.1007/s10549-019-05302-z. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 64.Fenton SE. 2006. Endocrine-disrupting compounds and mammary gland development: early exposure and later life consequences. Endocrinology 147(suppl 6):S18–S24, PMID: , 10.1210/en.2005-1131. [DOI] [PubMed] [Google Scholar]
  • 65.Brenner AV, Preston DL, Sakata R, Sugiyama H, Berrington de Gonzalez A, French B, et al. 2018. Incidence of breast cancer in the Life Span Study of Atomic Bomb Survivors: 1958–2009. Radiat Res 190(4):433–444, PMID: , 10.1667/RR15015.1. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 66.Cohn BA, Cirillo PM, Terry MB. 2019. DDT and breast cancer: prospective study of induction time and susceptibility windows. J Natl Cancer Inst 111(8):803–810, PMID: , 10.1093/jnci/djy198. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 67.Abreu AP, Kaiser UB. 2016. Pubertal development and regulation. Lancet Diabetes Endocrinol 4(3):254–264, PMID: , 10.1016/S2213-8587(15)00418-0. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 68.Biro FM, Pajak A, Wolff MS, Pinney SM, Windham GC, Galvez MP, et al. 2018. Age of menarche in a longitudinal US cohort. J Pediatr Adolesc Gynecol 31(4):339–345, PMID: , 10.1016/j.jpag.2018.05.002. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 69.Tiwary CM. 1998. Premature sexual development in children following the use of estrogen- or placenta-containing hair products. Clin Pediatr (Phila) 37(12):733–739, PMID: , 10.1177/000992289803701204. [DOI] [PubMed] [Google Scholar]
  • 70.Rivera-Núñez Z, Kinkade CW, Zhang Y, Rockson A, Bandera EV, Llanos AAM, et al. 2022. Phenols, parabens, phthalates and puberty: a systematic review of synthetic chemicals commonly found in personal care products and girls’ pubertal development. Curr Environ Health Rep 9(4):517–534, PMID: , 10.1007/s40572-022-00366-4. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 71.Giaquinto AN, Sung H, Miller KD, Kramer JL, Newman LA, Minihan A, et al. 2022. Breast Cancer Statistics, 2022. CA Cancer J Clin 72(6):524–541, PMID: , 10.3322/caac.21754. [DOI] [PubMed] [Google Scholar]
  • 72.Shoemaker ML, White MC, Wu M, Weir HK, Romieu I. 2018. Differences in breast cancer incidence among young women aged 20–49 years by stage and tumor characteristics, age, race, and ethnicity, 2004–2013. Breast Cancer Res Treat 169(3):595–606, PMID: , 10.1007/s10549-018-4699-9. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 73.Kong X, Liu Z, Cheng R, Sun L, Huang S, Fang Y, et al. 2020. Variation in breast cancer subtype incidence and distribution by race/ethnicity in the United States from 2010 to 2015. JAMA Netw Open 3(10):e2020303, PMID: , 10.1001/jamanetworkopen.2020.20303. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 74.Biro FM, Greenspan LC, Galvez MP, Pinney SM, Teitelbaum S, Windham GC, et al. 2013. Onset of breast development in a longitudinal cohort. Pediatrics 132(6):1019–1027, PMID: , 10.1542/peds.2012-3773. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 75.Zota AR, VanNoy BN. 2021. Integrating intersectionality into the exposome paradigm: a novel approach to racial inequities in uterine fibroids. Am J Public Health 111(1):104–109, PMID: , 10.2105/AJPH.2020.305979. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 76.Weinberg CR, Shore DL, Umbach DM, Sandler DP. 2007. Using risk-based sampling to enrich cohorts for endpoints, genes, and exposures. Am J Epidemiol 166(4):447–455, PMID: , 10.1093/aje/kwm097. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 77.Shen J, Liao Y, Hopper JL, Goldberg M, Santella RM, Terry MB. 2017. Dependence of cancer risk from environmental exposures on underlying genetic susceptibility: an illustration with polycyclic aromatic hydrocarbons and breast cancer. Br J Cancer 116(9):1229–1233, PMID: , 10.1038/bjc.2017.81. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 78.Carroll R, White AJ, Keil AP, Meeker JD, McElrath TF, Zhao S, et al. 2020. Latent classes for chemical mixtures analyses in epidemiology: an example using phthalate and phenol exposure biomarkers in pregnant women. J Expo Sci Environ Epidemiol 30(1):149–159, PMID: , 10.1038/s41370-019-0181-y. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 79.Elliott MR, Zhao Z, Mukherjee B, Kanaya A, Needham BL. 2020. Methods to account for uncertainty in latent class assignments when using latent classes as predictors in regression models, with application to acculturation strategy measures. Epidemiology 31(2):194–204, PMID: , 10.1097/EDE.0000000000001139. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 80.Rothman KJ. 1990. No adjustments are needed for multiple comparisons. Epidemiology 1(1):43–46, PMID: , 10.1097/00001648-199001000-00010. [DOI] [PubMed] [Google Scholar]
  • 81.Althouse AD. 2016. Adjust for multiple comparisons? It’s not that simple. Ann Thorac Surg 101(5):1644–1645, PMID: , 10.1016/j.athoracsur.2015.11.024. [DOI] [PubMed] [Google Scholar]
  • 82.O’Brien KM, Ogunsina K, Wentzensen N, Sandler DP. 2023. Douching and genital talc use: patterns of use and reliability of self-reported exposure. Epidemiology 34(3):376–384, PMID: , 10.1097/EDE.0000000000001589. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 83.Calafat AM, Valentin-Blasini L, Ye X. 2015. Trends in exposure to chemicals in personal care and consumer products. Curr Environ Health Rep 2(4):348–355, PMID: , 10.1007/s40572-015-0065-9. [DOI] [PubMed] [Google Scholar]
  • 84.Kessler R. 2015. More than cosmetic changes: taking stock of personal care product safety. Environ Health Perspect 123(5):A120–A127, PMID: , 10.1289/ehp.123-A120. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 85.Harley KG, Kogut K, Madrigal DS, Cardenas M, Vera IA, Meza-Alfaro G, et al. 2016. Reducing phthalate, paraben, and phenol exposure from personal care products in adolescent girls: findings from the HERMOSA intervention study. Environ Health Perspect 124(10):1600–1607, PMID: , 10.1289/ehp.1510514. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 86.Toxic-Free Cosmetics Act, AB 2762. 2020. California State Assembly, 2019–2020 Sess (Muratsuchi 2020) (Ca 2020). https://leginfo.legislature.ca.gov/faces/billNavClient.xhtml?bill_id=201920200AB2762 [accessed 19 December 2023].
  • 87.Toxic-Free Cosmetics Act, HB 1047-S. 2023. Washington State Legislature, 68th Legislature, 2023 Sess (Mena R, Berry, Simmons, Duerr, Goodman, Bateman, Reed, Fitzgibbon, Ramel, Doglio, Orwall, Macri, Gregerson, Thai, Stonier, Santos, Riccelli, Ormsby 2023) (Wa 2023). https://lawfilesext.leg.wa.gov/biennium/2023-24/Htm/Bills/Session%20Laws/House/1047-S.SL.htm [accessed 19 December 2023].

Associated Data

This section collects any data citations, data availability statements, or supplementary materials included in this article.

Supplementary Materials


Articles from Environmental Health Perspectives are provided here courtesy of National Institute of Environmental Health Sciences

RESOURCES