Description:
The recent Decision of the European Union (2017/848) to specifically include the Pelagic Habitat (HP) as well as certain criteria that must be considered to estimate its quality following the Marine Strategies Framework Directive (MSF; in particular with regard to Descriptor 1: Biodiversity) has revealed the existence of a large methodological and basic knowledge gap. At the moment there is no consensus regarding the definition of Good Environmental Status (GES) for HPs. However, it is essential to determine what qualities a PH must have in order to be considered in GES in order to create indicators that allow the monitoring and management objectives proposed in the DMEM to be met (Dickey-Collas et al. 2017).
One of the conditions that the HP must meet to meet the GES criteria is that all species present in normal environmental conditions must be able to find their HP necessary to complete their life cycle. Another condition that the HP must meet to be in GES is precisely that neither the physical dynamics of the ocean nor the movements of biota and water masses are obstructed (Dickey-Collas et al. 2017). Knowledge of the pelagic environment, hydrographic characteristics and dynamics of water bodies plays a fundamental role in understanding the processes that regulate both the dynamics of populations exploited by fishing (Alvarez-Berastegui et al. 2014) and marine diversity (Hidalgo et al. 2015). Such knowledge is therefore crucial for the evaluation and planning of management measures to ensure the sustainability of pelagic and demersal living resources. Time series of planktonic phases and hydrographic and biogeochemical variables (nutrients and dissolved oxygen) can be a very valuable tool for monitoring marine biodiversity and changes in water bodies. These changes can be used to determine indicators and threshold values that define the GES of a HP and its impact on biodiversity. Many species of fish in the Mediterranean have their laying season in spring-summer.
Spring-summer fish larvae data sets exist for most of the Mediterranean Geographic Sub-Areas (GSAs) described by the General Fisheries Commission of the Mediterranean. For most GSAs, there is also sufficient hydrographic information related to fish larvae to be able to cover the objectives regarding the establishment of ranges and thresholds proposed by EU Decision 2017/848: “The establishment of threshold values should take into account the dynamic nature of marine ecosystems and their elements, which can change in space and time due to hydrological and climatic variations, predator-prey relationships and other environmental factors. Threshold values should also reflect the fact that marine ecosystems can recover, if they are deteriorated, to a state that reflects the prevailing physiographic, geographical, climatic and biological conditions, rather than returning to a particular previous state.”
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