Does coastal lagoon habitat quality affect fish growth rate and their recruitment? Insights from fishing and acoustic surveys
Introduction
The evaluation of anthropogenic impacts on coastal lagoons requires efficient indicators of their ability to sustain ecosystem functioning and provide ecosystem services upon which human welfare depends such as protein supply. Moreover the European states have to achieve good environmental status of the EU's marine waters by 2020 and to protect the resource base upon which marine-related economic and social activities depend (EC, 2008). However, fishery–environment relationships are complex, and managing shallow water lagoon fisheries remains a difficult task (Breitburg et al., 2009; Brehmer et al., 2011a; Pérez-Ruzafa and Marcos, 2012). Fish have often been used to detect the disruption of marine and coastal ecosystems (e.g. Harmelin et al., 1995; Ramos Miranda et al., 2005; Villeger et al., 2010), and recently Rose et al. (2009) demonstrated the impact of hypoxia events on fish populations using modelling studies, while Stierhoff et al. (2006) focused on the ‘nursery quality’ of such critical habitats. More precisely, Stierhoff et al. (2009) used the RNA to DNA ratio to show that hypoxia events induce growth limitation in juvenile flatfishes, similarly as Brown-Peterson (2008) had observed with Palaemonetes pugio in an experimental study.
Since fish abundance has been recognized to be positively linked to the quality of habitats that promotes growth and survival of early life stages (Ross, 2003), the ecological status of estuaries and lagoons, offering food quantity and shelter for the larval and juvenile stages (Whitfield, 1999), is thus especially important to the sustainability of this resource. Indeed, high-quality coastal habitats, beyond their eutrophication and other physico-chemical characteristics, are also those where the abundance of juvenile fish is enhanced and fish growth optimized (Taylor et al., 2007). Using flatfish growth, size, body condition as well as population abundance, Gilliers et al. (2006) have assessed that bad habitat quality (chemical contamination) had a negative impact on biological performance.
We carried out a study in three shallow coastal lagoons in the South of France (Languedoc-Roussillon) along a gradient of habitat quality. The Languedoc-Roussillon lagoons occupy a total area of 40,000 ha, often exploited by small scale fisheries. Apart from recreational angling, the commercial fish catch amounts to ca.2000 metric tonnes per year (Guillou et al., 2002), with a total of 532 small fishing boats working in the regional lagoons. Mediterranean lagoons of this kind serve as important nursery areas for many fish including commercially important species such as Sparus aurata (Beck et al., 2001; Mercier et al., 2011). In a previous study, fishing surveys were performed to investigate fish abundances: initial findings suggested that the eutrophication level had no impact on fish diversity, even if an evidence of an impact on macrozoobenthic diversity was reported (Mouillot et al., 2005). We also assessed diagnostic estimators of the eutrophication level and ecotoxicity (Brehmer et al., 2006, 2011a) for these lagoons. The current study used an acoustic method to provide further information about pelagic fish characteristics; individual fish were detected using a fixed split-beam echo-sounder (e.g. Kubecka and Duncan, 1998a) with horizontal beaming. This paper uses data from both fishing and horizontal beaming acoustics surveys to investigate the relationship between habitat quality, defined here as the lagoon ecological status and toxicological effect of pesticides, and the abundance and size of lagoon fish.
Section snippets
Three shallow water lagoons and their habitat characteristics
Three Mediterranean lagoons (characterised by low tide amplitudes and a temperate climate) were studied (Fig. 1). They are located less than 19 km from each other along the same coast. The Or lagoon (Carnon-Pérols-Mauguio) has a total surface area of 3167 ha (average depth: 0.8 m), the Prévost lagoon (Palavas-les-flots) has an area of 380 ha (average depth: 0.3 m), and the Ingril lagoon (Frontignan) has an area of 549 ha (average depth: 0.6 m).
Differences in habitat quality were assessed by
Results
We estimated CPUE values of 543 and 932 kg per day for the Or and Prévost lagoons, respectively. Overall, we obtained a mean CPUE of 737 kg per day for the BHS lagoons, which was almost twice the value found in the Ingril GHS lagoon, i.e. 405 kg per day. Eels (Anguilla anguilla) constituted the bulk of the fish caught; their relative abundance was lowest in the GHS lagoon (Fig. 3). The Mugilidae group was the second most abundant after A. anguilla. They were present in all three lagoons
Discussion
Classical acoustic assessment methods (Simmonds and MacLennnan, 2005) are not suitable for use in very shallow water, both for logistic reasons due to water shallowness, and biological reasons, because of the obvious fish avoidance reaction to the approaching boat (Kubecka and Wittingerova, 1998b; Guillard et al., 2010). However, direct horizontal beaming acoustic observations in situ of fish population characteristics in very shallow lagoons (less than 1 m depth) have been shown to be useful
Acknowledgements
This study was funded by a grant provided by the Languedoc-Roussillon Region and the French state CPER XI coordinate by Prof. Thang Do Chi† (UMR ECOSYM) to who we dedicated this works. Additional data were provided by Ifremer observatory network (LER-LR, Sète). The final analysis was funded by the GIS Europole Mer (Plouzané, France), the AWA (BMBF-AIRD) project and done inside the Labex Mer. We would like to thank Prof. Andrew Bakun (University of Miami) for his early encouragement and the
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