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the humboldt current system of northern and central chile - figema

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THE HUMBOLDT CURRENT SYSTEM OF NORTHERN AND CENTRAL CHILEHCS (<strong>and</strong> in o<strong>the</strong>r EBCs) requires detailed underst<strong>and</strong>ing <strong>of</strong> <strong>the</strong> different components <strong>of</strong> <strong>the</strong>respective <strong>system</strong> (Moloney et al. 2005).Seabirds <strong>and</strong> marine mammalsIn marine environments seabirds <strong>and</strong> partially marine mammals are highly visible wide-ranging,upper trophic-level consumers. Upwelling <strong>system</strong>s are generally characterised by high production<strong>and</strong> relatively short food chains/webs, enabling massive energy transfer to <strong>the</strong> higher trophic levels(Cushing 1971, Arntz & Fahrbach 1991). The upwelling <strong>system</strong> <strong>of</strong> <strong>the</strong> Humboldt Current isparticularly well suited for studying <strong>the</strong> effects <strong>of</strong> <strong>the</strong> marine environment on <strong>the</strong> biology <strong>and</strong>ecology <strong>of</strong> seabirds <strong>and</strong> marine mammals.SeabirdsIn <strong>the</strong> HCS <strong>the</strong>re is a rich diversity <strong>of</strong> seabirds, comprising at least 14 breeding species, 9 <strong>of</strong> whichare endemic (Table 2). According to available information, along <strong>the</strong> coast <strong>of</strong> Chile <strong>the</strong> mostimportant breeding colonies are found on isl<strong>and</strong>s <strong>of</strong> nor<strong>the</strong>rn-<strong>central</strong> Chile, near upwelling areas.The grey gull (Larus modestus), which nests inl<strong>and</strong> in <strong>the</strong> Atacama Desert, travels to <strong>the</strong> coast ona daily basis to forage in <strong>the</strong> upwelling zones <strong>of</strong>f Ant<strong>of</strong>agasta (~23°S). Although proximity to afeeding ground is relevant in endemic seabirds, it seems that inaccessibility to predators <strong>and</strong> humanintrusion strongly determines <strong>the</strong> distribution <strong>of</strong> breeding populations. Despite some protectivestatus, most isl<strong>and</strong>s in <strong>the</strong> HCS are subject to human disturbance. In <strong>the</strong> past, this was causedmainly by guano harvesting <strong>and</strong> egg collecting. At present, introduced mammals <strong>and</strong> unregulatedtourism (Ellenberg et al. 2006) are a major problem.The majority <strong>of</strong> <strong>the</strong> endemic seabirds breed once a year. However, in <strong>the</strong>ir nor<strong>the</strong>rnmostbreeding areas (Peru), species such as <strong>the</strong> Humboldt penguin (Spheniscus <strong>humboldt</strong>i) nest throughout<strong>the</strong> year. Apparently, <strong>the</strong> two-peak breeding strategy has evolved in response to more favourableoceanographic <strong>and</strong> climatic conditions <strong>of</strong>f Peru, <strong>and</strong> this behaviour is preserved in nor<strong>the</strong>rn-<strong>central</strong>Chile providing additional <strong>of</strong>fspring to those produced during <strong>the</strong> spring event (Simeone et al.2002). Fur<strong>the</strong>rmore, differences in food availability along its breeding range (~4000 km) mightinduce lower breeding performance in sou<strong>the</strong>rn colonies <strong>of</strong> this species (Hennicke & Culik 2005).These birds feed on <strong>the</strong> main pelagic fish species from <strong>the</strong> HCS, mainly anchovy <strong>and</strong> jack mackerel.The proportion <strong>of</strong> fish stocks taken by endemic seabirds is not well known, but most likely doesnot exceed 10%. Incidental mortality <strong>of</strong> endemic seabirds due to fisheries is mainly caused by gillnets (Simeone et al. 1999, see also Majluf et al. 2002).The HCS is visited regularly by a number <strong>of</strong> migrant species. Among <strong>the</strong> Procelariiformes, whitechinnedpetrels (Procellaria aequinoctialis), Buller’s albatrosses (Thalassarche bulleri), Antarcticprions (Pachyptila desolata) <strong>and</strong> Juan-Fernández petrels (Pterodroma externa) are <strong>the</strong> most abundantspecies during austral summer (Weichler et al. 2004). There is evidence that <strong>the</strong> HCS is also frequentedby o<strong>the</strong>r remarkable visitors such as <strong>the</strong> Chatham, w<strong>and</strong>ering <strong>and</strong> royal albatrosses (Thalassarcheeremita, Diomedea exulans, <strong>and</strong> D. epomophora, respectively). Apparently <strong>the</strong> presence <strong>of</strong> <strong>the</strong>sespecies at such a distance from <strong>the</strong>ir colonies is related to <strong>the</strong> food abundance in <strong>the</strong> HCS, which insummer also attracts species like <strong>the</strong> black-browed albatross (Thalassarche melanophris) from sou<strong>the</strong>rnisl<strong>and</strong>s (56°S) (Arata & Xavier 2003) <strong>and</strong> during winter species like <strong>the</strong> white-chinned petrelsfrom South Georgia (Phillips et al. 2006). The abundances <strong>of</strong> some <strong>of</strong> <strong>the</strong>se visitors during australsummer may reach 2.5–5 birds km −2 , but at present it is not known which proportion <strong>of</strong> <strong>the</strong> entirepopulation <strong>of</strong> <strong>the</strong>se visitors may at times use <strong>the</strong> HCS as a feeding ground. The large albatrossesmainly feed on cephalopods <strong>and</strong> pelagic fishes (resulting in deadly interactions with long-line fisheries),221

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