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# (a) Residuals of Scaled Lean Mass Index (day 800) split by sex and early-life treatments (Control in blue and Imidacloprid in orange). Control (n = 20) = Ad libitum-Control + Restricted-Control / Imidacloprid (n = 16) = Ad libitum-Imidacloprid + Restricted-Imidacloprid). (b) Lean mass corrected Basal Metabolic Rate (model residuals) (day 800) according to the sex and the two treatments (Control and Imidacloprid). Specifications of the boxplots are provided in the caption of Figure 1. These results show individuals treated during the first half of the experiment. P-value ≤\documentclass[12pt]{minimal} \usepackage{amsmath} \usepackage{wasysym} \usepackage{amsfonts} \usepackage{amssymb} \usepackage{amsbsy} \usepackage{mathrsfs} \usepackage{upgreek} \setlength{\oddsidemargin}{-69pt} \begin{document}$$\le$$\end{document} 0.05*.

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... Several studies have demonstrated that contaminants can alter the functioning of the HPT axis and the metabolism of vertebrates (e.g., Braham & Neal, 1974), but most of these studies have focused on polychlorinated biphenyls (French et al., 2001;Smits et al., 2002;Tori & Mayer, 1981;Verreault et al., 2007;Voltura & French, 2000), organochlorine pesticides (Blévin et al., 2017), polybrominated diphenyl ethers (Allen et al., 2016;Lema Sean et al., 2008), per-and polyfluoroalkyl compounds (Ask et al., 2021;Blévin et al., 2017;Sebastiano et al., 2021), and neonicotinoids (Zgirski et al., 2021). The potential impact of endocrine disruptors on metabolism remains neglected, especially regarding contaminants of emerging interest such as azoles. ...
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