PMID- 25956003 OWN - NLM STAT- MEDLINE DCOM- 20160713 LR - 20240520 IS - 1552-9924 (Electronic) IS - 0091-6765 (Print) IS - 0091-6765 (Linking) VI - 123 IP - 10 DP - 2015 Oct TI - Brominated Flame Retardants and Other Persistent Organohalogenated Compounds in Relation to Timing of Puberty in a Longitudinal Study of Girls. PG - 1046-52 LID - 10.1289/ehp.1408778 [doi] AB - BACKGROUND: Exposure to hormonally active chemicals could plausibly affect pubertal timing, so we are investigating this in the Breast Cancer and the Environment Research Program. OBJECTIVES: Our goal was to examine persistent organic pollutants (POPs) in relation to pubertal onset. METHODS: Ethnically diverse cohorts of 6- to 8-year-old girls (n = 645) provided serum for measure of polybrominated diphenyl ethers (PBDEs), polychlorinated biphenyls (PCBs), organochlorine pesticides (OCPs), and lipids. Tanner stages [breast (B) and pubic hair (PH)], and body mass index (BMI) were measured at up to seven annual clinic visits. Using accelerated failure time models, we calculated time ratios (TRs) for age at Tanner stages 2 or higher (2+) and POPs quartiles (Q1-4), adjusting for confounders (race/ethnicity, site, caregiver education, and income). We also calculated prevalence ratios (PRs) of Tanner stages 2+ at time of blood sampling. RESULTS: Cross-sectionally, the prevalence of B2+ and PH2+ was inversely related to chemical serum concentrations; but after adjustment for confounders, only the associations with B2+, not PH2+, were statistically significant. Longitudinally, the age at pubertal transition was consistently older with greater chemical concentrations; for example: adjusted TR for B2+ and Q4 for SigmaPBDE = 1.05; 95% CI: 1.02, 1.08, for SigmaPCB = 1.05; 95% CI: 1.01, 1.08, and for SigmaOCP = 1.10; 95% CI: 1.06, 1.14, indicating median ages of about 6 and 11 months older than least exposed, and with similar effect estimates for PH2+. Adjusting for BMI attenuated associations for PCBs and OCPs but not for PBDEs. CONCLUSIONS: This first longitudinal study of puberty in girls with serum POPs measurements (to our knowledge) reveals a delay in onset with higher concentrations. FAU - Windham, Gayle C AU - Windham GC AD - California Department of Public Health, Richmond, California, USA. FAU - Pinney, Susan M AU - Pinney SM FAU - Voss, Robert W AU - Voss RW FAU - Sjodin, Andreas AU - Sjodin A FAU - Biro, Frank M AU - Biro FM FAU - Greenspan, Louise C AU - Greenspan LC FAU - Stewart, Susan AU - Stewart S FAU - Hiatt, Robert A AU - Hiatt RA FAU - Kushi, Lawrence H AU - Kushi LH LA - eng GR - U01 ES012770/ES/NIEHS NIH HHS/United States GR - U01 ES12770/ES/NIEHS NIH HHS/United States GR - UL1 RR024131/RR/NCRR NIH HHS/United States GR - P30 ES006096/ES/NIEHS NIH HHS/United States GR - P30-ES006096/ES/NIEHS NIH HHS/United States GR - U01 ES012801/ES/NIEHS NIH HHS/United States GR - U01ES012801/ES/NIEHS NIH HHS/United States GR - U01 ES019435/ES/NIEHS NIH HHS/United States PT - Journal Article PT - Research Support, N.I.H., Extramural PT - Research Support, Non-U.S. Gov't DEP - 20150508 PL - United States TA - Environ Health Perspect JT - Environmental health perspectives JID - 0330411 RN - 0 (Endocrine Disruptors) RN - 0 (Environmental Pollutants) RN - 0 (Flame Retardants) RN - 0 (Halogenated Diphenyl Ethers) RN - 0 (Hydrocarbons, Chlorinated) RN - 0 (Pesticides) RN - DFC2HB4I0K (Polychlorinated Biphenyls) SB - IM CIN - Environ Health Perspect. 2015 Oct;123(10):A266. PMID: 26421753 MH - Breast/drug effects/growth & development MH - California MH - Child MH - Endocrine Disruptors/blood MH - *Environmental Exposure MH - Environmental Monitoring MH - Environmental Pollutants/*blood MH - Female MH - Flame Retardants/analysis MH - Hair/drug effects/growth & development MH - Halogenated Diphenyl Ethers/*blood MH - Humans MH - Hydrocarbons, Chlorinated/*blood MH - Longitudinal Studies MH - Ohio MH - Pesticides/blood MH - Polychlorinated Biphenyls/blood MH - Puberty/*drug effects PMC - PMC4590751 COIS- The contents of this report are solely the responsibility of the authors and do not necessarily represent the official views of the NIEHS, the NCI, the Centers for Diseases Control and Prevention, or the CDPH. G.C.W. is employed by EHIB/CDPH; R.W.V. was employed by Impact Assessment Inc., at the time the work was completed; L.C.G. is employed by Kaiser Permanente Medical Care Program; and L.H.K. is employed by the Division of Research, Kaiser Permanente. The authors declare they have no actual or potential competing financial interests. EDAT- 2015/05/09 06:00 MHDA- 2016/07/14 06:00 PMCR- 2015/10/01 CRDT- 2015/05/09 06:00 PHST- 2014/06/03 00:00 [received] PHST- 2015/05/06 00:00 [accepted] PHST- 2015/05/09 06:00 [entrez] PHST- 2015/05/09 06:00 [pubmed] PHST- 2016/07/14 06:00 [medline] PHST- 2015/10/01 00:00 [pmc-release] AID - ehp.1408778 [pii] AID - 10.1289/ehp.1408778 [doi] PST - ppublish SO - Environ Health Perspect. 2015 Oct;123(10):1046-52. doi: 10.1289/ehp.1408778. Epub 2015 May 8.