animals requires the use of non-invasive sampling methods that allow the quantification of Hg without euthanizing the individuals of these endangered species (Bezerra et al. 2012;Rodriguez et al. 2019). Many authors worldwide (Sakai et al. 2000;Day et al. 2005;Bezerra et al. 2012Bezerra et al. , 2013 have successfully used scutes to monitor Hg in these chelonians. For example, scutes were used to characterize bioaccumulation and patterns of temporal exposure to Hg and other trace metals in sea turtles (Schneider et al. 2015; Bezerra et al. 2015; Barraza et al. 2019; Villa et al. 2019) collected for two populations of C. mydas from a foraging ground within the Great Barrier Reef (Howick Island group) as well as from Shoalwater Bay in Australia and their results provided robust proxies of exposure conditions. Similarly, Hg concentrations in scutes reflected exposure levels in C. caretta from different nesting areas in northeastern Brazil (Barrios et al. 2019).Sea turtle carapace scutes grow in a layered pattern and with multiple growth areas (Achrai and Wagner 2013), because of that, the accumulation of elements can vary across carapace areas (Day et al. 2005;Mattei et al. 2015). Structurally, the carapace is subdivided into four areas and