Medidas de Gestao das Pescarias Marinhas e Aquicultura 2019 The State of World Fisheries and Aquaculture 2018 | Page 118

PART 2 FAO FISHERIES AND AQUACULTURE IN ACTION and most of them already have such conser vation and management measures in place. 17 environmental, social and economic. An erosion of biodiversit y would not only affect the structure and function of ecosystems (see also “Blue growth in action” in Part 4), but would also impair the potential for such systems to adapt to new challenges such as population growth and climate change (see “Climate change impacts and responses” in Part 3). In the past few decades, the role of biodiversit y in supporting a number of critical ecosystem ser vices has gained more and more attention (Beaumont et al., 2007). Most recently, a number of governments have made international commitments to conser vation of marine biodiversit y within the framework of the 2030 Agenda and the Convention on Biological Diversit y (CBD). IUU fishing has been reduced in areas regulated by some RFMOs over the years. RFMOs that continue to face challenges in this respect are applying recommendations from performance reviews and developing new MCS tools, using CDSs and implementing or considering regional vessel monitoring systems (VMSs). Some RFMO Contracting Parties carry out patrolling and radar satellite surveillance. Collaboration among RFMOs, other organizations and agencies facilitates and supports efforts to combat IUU fishing. RFMOs are strategically positioned to coordinate efforts with key stakeholders in their respective regions to enforce necessary measures. n Area-based management measures in coastal areas and inland waters BIODIVERSITY, FISHERIES AND AQUACULTURE A number of both static and dynamic area-based management tools are used to support the conser vation of biodiversit y, enhancing countries’ abilit y to implement the ecosystem approach to fisheries (discussed in the last section of Part 2). Spatial and temporal fishing restrictions, including long-term ”no-take” closures, have a long histor y of use in fisheries alongside a range of other measures, and predate the current concept of aquatic protected areas for biodiversit y conser vation. More recently, with an increase in ocean technolog y and the abilit y to acquire information in real time, other concepts such as dynamic ocean management have gained increasing traction (Dunn et al., 2016), offering great promise for the sustainable management of ocean resources. The world’s aquatic ecosystems are structurally and functionally highly biodiverse, a vital web of thousands of interconnected species which support fisheries and aquaculture, contributing to the nutritional, economic, social, cultural and recreational betterment of human populations (Box 8). All phyla but one are found in the oceans (34 phyla), compared to 15 phyla that are found on land. Aquatic biodiversit y is sustained in the wild across marine (oceans, seas, estuaries), brackish and freshwater (lakes, reser voirs, rivers, rice paddies and other wetlands) environments, as well as in culture within managed production systems. Freshwater ecosystems, although they contain less than 1 percent of all water, hold about 40 percent of the world’s fish species (Balian et al., 2008). Protected areas Aquatic protected areas, including marine protected areas (MPAs), were initially introduced in the context of biodiversit y conser vation to protect aquatic ecosystems and reverse the degradation of their habitats, and are increasingly promoted by the environment sector as a complement to fisheries management measures to address overfishing and unsustainable resource utilization (FAO, 2011b). A number of international policy instruments have recently been established in support of marine protected areas. Aichi target 11 and SDG target 14.5, in particular, aim for the designation of 10 percent Maintaining biodiversit y is critical to meeting the objectives of the three pillars of sustainabilit y – 17  RFMOs surveyed: Commission for the Conservation of Antarctic Marine Living Resources (CCAMLR); General Fisheries Commission for the Mediterranean (GFCM); Inter-American Tropical Tuna Commission (IATTC); Indian Ocean Tuna Commission (IOTC); Northwest Atlantic Fisheries Organization (NAFO); North Atlantic Salmon Conservation Organization (NASCO); North-East Atlantic Fisheries Commission (NEAFC); North Pacific Anadromous Fish Commission (NPAFC); North Pacific Fisheries Commission (NPFC); Regional Commission for Fisheries (RECOFI); South East Atlantic Fisheries Organisation (SEAFO); South Indian Ocean Fisheries Agreement (SIOFA). | 102 |