Just Cerfing Vol. 7, Issue 8, August 2016 Volume 5, Issue 3, March, 2014 | Page 60

Previous Page Table of Contents Next Page Effects of the Discharge of Iron Ore Tailings the south of Ecuador. The rest of the region has moderate indices, the main threads for biodiversity being fisheries, pollution, urban development, mine exploitation, oil industries, aquaculture, marine transport, invasive species, and climate change. From a world perspective, Latin America has occupied for long time an intermediate position, with a lower level of urbanization than Europe, North America, and Oceania but a higher level than Asia and Africa (Browning, 1958). The Latin American population, with ca. 380 million people, is concentrated in cities close to the coast whose development has been accompanied by increasing human activities and an exponential demand of infrastructure, industrialization, and tourism (Barragán, 2001). The model replicates what has been already experienced in the developed world with bad consequences: investors looking for fast benefits, without consideration for social development and environmental protection, and without considering scientific knowledge (Dias et al., 2012). Habitat disruption because of expanding aquaculture, agriculture, and other activities, such as the discharge of wastewaters, are among the most common environmental effects on South American coasts, degrading mangroves, estuaries, and coral reefs (Campuzano et al., 2011). While the development of the fisheries, aquaculture, and industrialization is relatively low, tourism on the coasts has become one of the most dynamic activities in Latin America (Fayissa, Nsiach, and Tadesse, 2009; Lionetti and González, 2012). This diagnosis coincides with what was reported 10 years earlier by the Global Programme of Action for the Protection of the Marine Environment from Land-based Activities from the United Nations Environment Programme (UNEP), which highlighted the main environmental problems for South America: (a) inappropriate discharge of urban wastewater; (b) pollution by industrial discharge; (c) degradation of aquatic environments because of urban expansion; (d) inadequate disposal of solid waste; (e) activities related to the extraction, transport, and storage of oil and its derivates (Marcovecchio, 2000). Mining activities, especially, including the oil industry, generate important impacts on coastal zones, as in the case of coal in Brazil, aluminum in Surinam and Guyana, copper in Chile and Panamá, oil in Venezuela, 60 and gold in Nicaragua, Honduras, and Guatemala, with additional effects through the expansion or construction of ports necessary for the export of their products (Barragań, 2001; Escobar, 2002). Nevertheless, in Latin America the ca. 700 protected marine areas, which cover more than 300,000 km2, representing 1.5% of the coastal and continental waters (Guarderas, Hacker, and Lubchenco, 2008), are evidence of a coastal zone with a rich biodiversity, comprising 27 ecoregions (Chatwin and Rybock, 2007; Spalding et al., 2006; Sullivan-Sealy and Bustamante, 1999). Diverse regional inventories, developed for the southeastern Pacific (Chile, Perú, Ecuador, Colombia, and Panamá) during the last decade by the Permanent Commission for the Southern Pacific and others (DIRECTEMAR, 2007; see CPPS, 2012, for review) are evidence of a coast affected by domestic and industrial wastewater discharges, especially in Perú and Chile (Sanchez and Orozco, 1996). In the region, industrial activity contributes, with discharges of high organic content coming mainly from processing plants and canneries of fishery products, followed by the food industry, as well as extraction, exploitation, and construction involving soil movement (agriculture, forestry, and mining; GESAMP, 2001), with many contaminants reaching the sea through more than 100 rivers. The mining industry contributes in the region with inert sediments that can be very stable in chemical terms and grain size varying from silt to fine sands, as well as heavy metals, quicksilver, cyanide, acid waters, sulfates, and carbonates. Once these pollutants are disposed of in the sea, they alter the temperature and pH, thus altering biological cycles and the entire ecosystem (Escobar, 2002). In Chile, increasing urbanization along the coast has produced an increase in direct and indirect discharge of waste into the sea that, according to the CPPS, is the highest among the countries of the South American Pacific (DIRECTEMAR, 2007). Along the Chilean coast, more than 300 industrial plants affect the marine environment, with those generating the greatest effects in the mining industry in the north, cellulose industry in the south, and fishery industries in the center and south (Andrade et al., 2010; OCDE, 2005; Sanchez and Orozco, 1996). Additionally, the Chilean coast is full Just Cerfing Vol. 5, Issue 3, March 2014 Continued on Next Page 61