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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 CHILESeaward <strong>and</strong> alongshore exportation <strong>of</strong> larvae in river plumes, filaments <strong>and</strong> eddies seems tobe a common feature along <strong>the</strong> HCS. In nor<strong>the</strong>rn Chile, a mixture <strong>of</strong> coastal <strong>and</strong> <strong>of</strong>fshore larvalfishes, both in <strong>the</strong> coastal <strong>and</strong> adjacent <strong>of</strong>fshore areas, has been repeatedly reported in differentseasons <strong>and</strong> years (Loeb & Rojas 1988, Rojas et al. 2002, Rodríguez-Graña et al. 2005). Besides<strong>the</strong> existence <strong>of</strong> a narrow continental shelf, at least three oceanographic processes involving larvaltransport have been advocated to explain such patterns: (1) seaward surface Ekman transport <strong>and</strong>upwelling plumes, (2) <strong>the</strong> presence <strong>of</strong> filaments, <strong>and</strong> (3) warm-water intrusion during EN years,all well-documented processes in nor<strong>the</strong>rn Chile (González et al. 2000b, Sobarzo & Figueroa 2001).In <strong>central</strong> Chile, surface Ekman transport <strong>and</strong> cold-water filaments have also been reported to exportchl-a, meroplankton <strong>and</strong> ichthyoplankton from <strong>the</strong> coastal zone (Cáceres 1992, Morales et al. inreview) <strong>and</strong> <strong>the</strong>y have been used to explain part <strong>of</strong> <strong>the</strong> larval mortality rate estimations in <strong>the</strong> coastalzone (Castro & Hernández 2000, L<strong>and</strong>aeta & Castro 2006). Larval transport associated with riverplumes, mesoscale processes not occurring in nor<strong>the</strong>rn Chile, has also been proposed as a determinant<strong>of</strong> barnacle larval transport (Vargas et al. 2006c). Such plumes are also potential areas <strong>of</strong>increased larval food availability at <strong>the</strong> frontal area. O<strong>the</strong>r still-unknown oceanographic processescapable <strong>of</strong> transporting larval forms alongshore probably occur in <strong>the</strong> HCS. In fact, it is worthnoting that almost no reports exist on <strong>the</strong> role <strong>of</strong> <strong>the</strong> Humboldt Current itself or <strong>the</strong> Chile-Perupoleward under<strong>current</strong> as a means <strong>of</strong> alongshore latitudinal larval transport (except for potentialtransport <strong>of</strong> larval Pleuroncodes monodon in subsurface waters <strong>of</strong>f <strong>central</strong> Chile; Yannicelli 2005).In summary, a number <strong>of</strong> larval transport processes have been described along <strong>the</strong> <strong>central</strong> <strong>and</strong>sou<strong>the</strong>rn part <strong>of</strong> HCS. Three <strong>of</strong> <strong>the</strong>m seem particularly important when considered from anecological perspective: (1) larval transport (seaward <strong>and</strong> shoreward) in <strong>the</strong> surface Ekman layer,(2) exportation from <strong>the</strong> coast in filaments (especially <strong>of</strong>f <strong>the</strong> Mejillones Peninsula in nor<strong>the</strong>rnChile <strong>and</strong> <strong>of</strong>f <strong>the</strong> Talcahuano area <strong>of</strong> <strong>central</strong> Chile) <strong>and</strong> (3) <strong>the</strong> coastward subsurface larval transportin upwelling waters in spring <strong>and</strong> summer with <strong>the</strong> concomitant mixing <strong>of</strong> <strong>of</strong>fshore <strong>and</strong> coastalspecies near shore. Examples <strong>of</strong> important differences between nor<strong>the</strong>rn <strong>and</strong> <strong>central</strong> Chile are <strong>the</strong>influence <strong>of</strong> oceanographic processes such as EN events (much stronger in nor<strong>the</strong>rn Chile) <strong>and</strong> <strong>of</strong>river plumes (absent in nor<strong>the</strong>rn Chile). Overall, populations <strong>of</strong> invertebrates <strong>and</strong> fishes along <strong>the</strong>HCS develop multiple strategies to cope with <strong>the</strong> intense periods <strong>of</strong> transport during early lifestages. Timing <strong>the</strong> reproductive seasons with specific oceanographic events is most common.However, specific reproductive timing depends on <strong>the</strong> local sites <strong>of</strong> reproduction, capability <strong>of</strong>larvae to move vertically in <strong>the</strong> water column, length <strong>of</strong> larval life history/cycle <strong>and</strong> o<strong>the</strong>r not sowell studied processes (i.e., retention in upwelling shadows) or those occurring during <strong>the</strong> adultlife stage (seasonal growth, energy accumulation, oogenesis) that may finally affect <strong>the</strong> larvalcharacteristics mentioned above.Life-history adaptations <strong>of</strong> macroalgaeThe macroalgal flora along <strong>the</strong> HCS is characterised by <strong>the</strong> presence <strong>of</strong> endemic species (32%) mixedwith species <strong>of</strong> different biogeographical affinities, including subantarctic (34%), widely distributed(23%), tropical (3.5%) <strong>and</strong> amphi-equatorial (7%) species (Santelices 1980). In general, this speciescomposition, which is comparatively poorer than that reported for o<strong>the</strong>r regions <strong>and</strong> increases innumber toward higher latitudes (Lüning 1990, Santelices & Marquet 1998), responds to <strong>the</strong> relativebiogeographic isolation as a consequence <strong>of</strong> <strong>the</strong> predominant direction <strong>of</strong> <strong>the</strong> water circulation regimein <strong>the</strong> HCS (Santelices et al. 1980, Meneses & Santelices 2000). However, an increasing number <strong>of</strong>invasive species as a result <strong>of</strong> human activities (ship transport, aquaculture, etc.) has recently beenreported with concern about <strong>the</strong>ir impact on indigenous species (Castilla et al. 2005a). For example,recent surveys indicate an increase <strong>of</strong> subtropical elements, a decrease in endemic species <strong>and</strong> twobreak points in species composition at 12°S <strong>and</strong> 42°S (Meneses & Santelices 2000).273

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