Evaluation of trace elements in feathers of young kelp gull Larus dominicanus along the coast of Santa Catarina, Brazil
Introduction
The presence of metals in marine ecosystems is related to natural processes (e.g., rock weathering and soil leaching), but urbanization and industrialization are the main anthropogenic sources of trace elements threatening the health of these environments on both a local and large scale (Furness and Monaghan, 1987; Kennish, 1996; Förstner and Wittmann, 1981). One of the main problems is contamination by polycyclic aromatic hydrocarbons (Celino and Queiroz, 2006). Elevated levels of zinc (Zn) and cadmium (Cd) of industrial origins can also be found along with magnesium (Mg) contamination from urban stormwater drainage, which can alter the natural cycles of these elements (Barcellos et al., 1991; Marins et al., 2004; Scherer et al., 2015).
In this context, chemical pollution is a growing issue for ocean ecosystems, where apex predators bioaccumulate persistent chemical pollutants such as non-essential trace elements. The trophic position is, thus, a key aspect when assessing the impacts of environmental pollution on the oceans (Moura et al., 2018a). At low concentrations, trace metals such as copper (Cu), iron (Fe), manganese (Mn) and Zn contribute to the development of organisms, but non-essential metals such as Cd, chromium (Cr), lead (Pb) and mercury (Hg) are potentially toxic, especially to seabirds (Furness and Monaghan, 1987; Burger and Gochfeld, 1992). Seabirds can be affected by Hg contamination and this element may work as an important stress factor culminating in high mortality when these birds are in a condition of poor health (Fort et al., 2015).
Organisms can be contaminated via several routes such as respiration, skin contact but mainly through feeding (Burger and Gochfeld, 2002; Burger and Gochfeld, 2004), and the level of contamination is aggravated through bioaccumulation and biomagnification. Thus, seabirds can be used as indicators of environmental quality (Furness and Monaghan, 1987; Walsh, 1990; Burger, 1993; Burger and Gochfeld, 2001; Burger and Gochfeld, 2004; Ikemoto, 2005; Barbieri, 2009; Costa et al., 2013) by reflecting ecosystem health and are known as ocean sentinels (Boersma et al., 2001). In this context, non-invasive methods of acquiring samples, such as feather collection, have been successfully used in biomonitoring studies focused on the analysis of metals (Denneman and Douben, 1993). The trace elements accumulate in these structures, where they bind to proteins during feather formation (Burger and Gochfeld, 2002). One positive aspect of using feathers is this method does not cause injury to birds and they can quickly regenerate again.
Because they are represented throughout the trophic chain, seabirds are vulnerable to environmental contamination (Burger, 1993; Metcheva et al., 2005; Siciliano et al., 2005; Ruiz, 2008; Burger et al., 2000); thus, they have been used to monitor changes at the individual (acute effects) and populational (chronic effects) levels (Arias et al., 2007). By acting as trackers of contamination, seabirds also make it possible to diagnose the temporal and geographic patterns of oil spills (Furness and Camphuysen, 1997; Wiese and Ryan, 2003; Garcia-Borboroglu et al., 2006).
Half the global population is distributed along coastal regions (Hinrichsen and Robey, 2000; Fleming et al., 2006), which affects the natural balance of these areas (Förstner and Wittmann, 1981; Hax, 2000). In this context, the Santa Catarina coast, which accounts for 39% of the total area of the state of Santa Catarina, concentrates approximately 68% of the entire population of the state, which threatens the balance of this ecosystem (Lopes and Dias, 1996). This is because it receives inputs from rivers that, together with continental drainage, carry pollutants and put the marine environment at risk (Furness and Monaghan, 1987; Schreiber and Burger, 2001; Burger and Gochfeld, 2004).
This study evaluated the trace element (Cr, Pb, Zn and Hg) contaminations in the feathers of young Larus dominicanus captured on three coastal islands of the state of Santa Catarina, Brazil. The results were important to understand this species as a bioindicator of pollution in environment.
Section snippets
Study site
From May 2011 to November 2013, monthly sampling campaigns were conducted on three coastal islands off the coast of Santa Catarina. The Tamboretes Archipelago (26°22′10″S, 48°31′11″W) is located along the northern coast of the state, approximately 5 km from the mainland (Branco, 2003), and is part of Acaraí State Park, which was established in 2005. Pássaros Island, where the feather samples were collected, was used as a representative of the archipelago (Fig. 1). The Moleques do Sul
Results
During the study period 27 samples of young gull feathers were collected: 11 from Tamboretes, eight from Moleques do Sul and eight from Lobos (Table 3). The observed values did not present a normal distribution. Thus, the medians and maximum values are presented.
According the graphs for the Pb concentration, the larger median (2.1310 μg g−1) and maximum value (2.4480 μg g−1) was found in Lobos island (Fig. 2a). For all islands, the Cr values were below the quantification limit (0.0300 μg g−1) (
Discussion
As top predators in a marine food web seabirds are particularly susceptible to metal contamination affected by pollutants according to different diets and feeding strategies (Barbieri et al., 2007; Barbieri et al., 2010; Michelutti et al., 2010; Moura et al., 2018a) which easily accumulate in tissues (Mansouri et al., 2012). Also, an extensive range of environmental disturbances might cause differences in metal concentration (Moura et al., 2018b). Among the metals analyzed in this study, the Cr
CRediT authorship contribution statement
Dr. Luis Augusto Ebert: As a principal researcher my principal contributions were about the concept of this Project and the ideas and developing. The methodology was replicated from similar research, however, the way in which seabirds were captured and also the study sites were unprecedented. Regarding the validation of results, this project was part of my doctoral course and has already been validated by a committee of other researchers. Part of this doctoral work also involves the
Declaration of competing interest
The authors declare that they have no known competing financial interests or personal relationships that could have appeared to influence the work reported in this paper.
Acknowledgements
This study was funded by the National Council for Scientific and Technological Development (Conselho Nacional de Desenvolvimento Científico e Tecnológico - CNPQ), Brazil, under the concession of the doctoral scholarship number 141672/2011-0. All field activities were conducted with support from the Leonardo da Vinci University Centre (UNIASSELVI), FREITAG Laboratories and the Marine Birds Project (www.avesmarinhas.com.br), UNIVALI.
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