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the humboldt current system of northern and central chile - figema

the humboldt current system of northern and central chile - figema

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THE HUMBOLDT CURRENT SYSTEM OF NORTHERN AND CENTRAL CHILEO<strong>the</strong>r species introduced to <strong>the</strong> coast <strong>of</strong> Chile are abalone, originating from California <strong>and</strong>Japan. These have been mainly cultured in l<strong>and</strong>-based facilities, but due to an increasing production<strong>and</strong> limited holding capacities on l<strong>and</strong>, sea-based culture (as already established in sou<strong>the</strong>rn Chile)is also considered for nor<strong>the</strong>rn-<strong>central</strong> Chile. The production <strong>of</strong> abalones increased from 1 t in1998 to 342 t in 2005, <strong>and</strong> for <strong>the</strong> year 2006 it is expected that <strong>the</strong> Chilean abalone industry willproduce >500 t. Only in Region IV, <strong>current</strong>ly five abalone production centres are established <strong>and</strong>an additional five centres have solicited permits to initiate new aquaculture activities during 2006.The present abalone production in Chile is mainly based on <strong>the</strong> red abalone (Haliotis rufescens).However, <strong>the</strong> Japanese abalone (H. discus hannai), which has a better market value, is also raised,but to a lesser degree since culture technology has higher requirements (<strong>and</strong> costs) than those forred abalone.Although <strong>the</strong> l<strong>and</strong>-based abalone culture is not directly affected by variations in environmentalconditions, ENs may have severe effects on abalone culture because <strong>the</strong>y can produce strong impactson <strong>the</strong> population <strong>of</strong> large kelp, <strong>the</strong> main food resource presently used in abalone culture. The lackin supply <strong>of</strong> fresh food algae may produce serious bottlenecks in <strong>the</strong> culture <strong>of</strong> abalone. Some <strong>of</strong><strong>the</strong>se problems are occurring presently <strong>and</strong> <strong>the</strong> National Fisheries Service (SERNAPESCA) isconcerned with <strong>the</strong> overexploitation <strong>of</strong> kelp, restricting <strong>the</strong> extraction from natural kelp beds <strong>and</strong>promoting research for cultivation <strong>and</strong> management <strong>of</strong> seaweeds. This scenario presents importantchallenges for applied research in <strong>the</strong> near future.In general, aquaculture in nor<strong>the</strong>rn <strong>and</strong> <strong>central</strong> Chile does not reach <strong>the</strong> levels it has in sou<strong>the</strong>rnChile. Some <strong>of</strong> <strong>the</strong> main reasons for this are related to <strong>the</strong> fact that <strong>the</strong> coast <strong>of</strong> nor<strong>the</strong>rn Chile is(1) mostly exposed to wave action <strong>and</strong> (2) is strongly affected by important interannual variationsin oceanographic conditions. Future efforts should probably focus on <strong>the</strong> development <strong>of</strong> l<strong>and</strong>basedculture facilities <strong>and</strong> integrated <strong>system</strong>s where animals <strong>and</strong> algae are produced in combination(Chopin et al. 2001).Conservation <strong>of</strong> marine biodiversity<strong>and</strong> Marine Protected AreasThe HCS extending from Ecuador to sou<strong>the</strong>rn Chile is considered as one <strong>of</strong> <strong>the</strong> large marineeco<strong>system</strong>s for high-priority attention (Boersma et al. 2004). The growing use <strong>of</strong> coastal areas byhuman activities is also increasingly threatening marine biodiversity in <strong>the</strong> HCS. The most importantthreats are overfishing, aquaculture, pollution by sewage <strong>and</strong> mining activities, run<strong>of</strong>fs <strong>of</strong> chemicalsused for agriculture, oil spills <strong>and</strong> tourism activities (Vásquez et al. 1999, Fernández et al. 2000).All countries, including Chile, that have ratified <strong>the</strong> Convention on Biological Diversity (CBD)treaty agreed to develop a network <strong>of</strong> Marine Protected Areas (MPAs, as defined by IUCN 1994)to ultimately protect 10% <strong>of</strong> <strong>the</strong> marine environments by 2012, based on an eco<strong>system</strong> approach(Wood 2006). However, <strong>the</strong> actual establishment rate <strong>of</strong> MPAs (4.5% annual increase) reveals that<strong>the</strong> work plan is unrealistic <strong>and</strong> will not be achieved before <strong>the</strong> second half <strong>of</strong> this century (Wood2006). The Chilean case is a paradox as its economic exclusive zone (EEZ) corresponds to 17.8%<strong>of</strong> <strong>the</strong> Latin-American EEZ <strong>and</strong> is three times larger than its terrestrial territory (~18% <strong>of</strong> which isalready protected; Pauchard & Villarroel 2002). However, only 0.03% <strong>of</strong> <strong>the</strong> Chilean EEZ (0.67%<strong>of</strong> <strong>the</strong> territorial sea) is protected as MPAs (CONAMA personal communication). Fur<strong>the</strong>r, only14% <strong>of</strong> <strong>the</strong> surface area <strong>of</strong> <strong>the</strong>se MPAs are located within <strong>the</strong> HCS <strong>of</strong> nor<strong>the</strong>rn <strong>and</strong> <strong>central</strong> Chile(18°S to 41°S). Considering that ~95% <strong>of</strong> <strong>the</strong> Chilean population is located between 18°S <strong>and</strong> 41°S<strong>and</strong> <strong>the</strong> growing human impact in coastal areas, this zone represents one <strong>of</strong> <strong>the</strong> greatest challengesfor marine conservation.The Chilean fisheries management policy, through creation <strong>of</strong> Management <strong>and</strong> ExploitationAreas (AMERBs) for benthic resources from coastal habitats, is focusing on economically important295

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