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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 CHILE<strong>and</strong> heteromorphic phase expressions. Processes such as coalescence <strong>of</strong> spores (Santelices et al.1999, 2003), regrowth from crusts or vegetative propagation (Hannach & Santelices 1985, Gómez& Westermeier 1991, Macchiavello et al. 2003), selective mortality <strong>of</strong> early developmental stages(Martínez & Santelices 1998), differential phase ratios (Vega & Meneses 2001) <strong>and</strong> synchronisation<strong>of</strong> spore release (Edding et al. 1993, Tala et al. 2004) have been described in algae from nor<strong>the</strong>rn<strong>central</strong>Chile, which are related to potential selection under changing environmental conditions.While <strong>the</strong> seasonal <strong>and</strong> latitudinal gradients in environmental conditions along <strong>the</strong> HCS arerecognisable, <strong>the</strong> magnitude <strong>of</strong> <strong>the</strong>ir impact on <strong>the</strong> physiological <strong>and</strong> reproductive biogeography<strong>of</strong> benthic algae remains diffuse. Therefore, comparative studies focused on assemblages fromdifferent sites along <strong>the</strong> HCS are needed in order to define, for example, <strong>the</strong> environmentalthresholds involved in reproductive fitness, physiological adaptation <strong>and</strong> recovery capacity.A special case: enhanced solar radiationOzone depletion (with <strong>the</strong> concomitant increase <strong>of</strong> UV-B radiation) over <strong>the</strong> Antarctic region, whichin spring can reach areas as far north as 36°S, has opened <strong>the</strong> debate about its consequences on<strong>the</strong> marine biota <strong>of</strong> cold <strong>and</strong> temperate regions (Madronich et al. 1995, Sobolev 2000). Shortwavelengths (UV-B) affect photosyn<strong>the</strong>sis in different ways <strong>and</strong> have detrimental effects on DNA<strong>and</strong> o<strong>the</strong>r key cell components (Bisch<strong>of</strong> et al. 2006). Recent studies indicate a potential impact <strong>of</strong><strong>current</strong> solar UV radiation on photosyn<strong>the</strong>sis <strong>of</strong> intertidal macroalgae from <strong>the</strong> sou<strong>the</strong>rn limit <strong>of</strong>HCS (39°S; Gómez et al. 2004, Huovinen et al. 2006). In nor<strong>the</strong>rn Chile (30°S), zoospores, gametophytes<strong>and</strong> embryonic sporophytes <strong>of</strong> subtidal Lessonia trabeculata <strong>and</strong> <strong>the</strong> intertidal L. nigrescensshow elevated sensitivity to UV exposure, leading to high spore mortalities <strong>and</strong> decreases ingermination under <strong>current</strong> UV doses (Véliz et al. 2006). In general, UV sensibility <strong>of</strong> early stagescorrelates with <strong>the</strong> depth-distribution patterns <strong>of</strong> <strong>the</strong> parental sporophytes, suggesting that this factormay play a relevant role in depth zonation <strong>of</strong> benthic algae in this region (Gómez et al. 2005b).Recent surveys indicate that intertidal species display various photoprotective mechanisms, inparticular <strong>the</strong> ‘dynamic photoinhibition’, regarded as a down-regulation <strong>of</strong> <strong>the</strong> photosyn<strong>the</strong>ticapparatus to quench <strong>the</strong> impact <strong>of</strong> excess energy (Gómez et al. 2004). Some intertidal algae alsohave noticeably high contents <strong>of</strong> UV-absorbing substances (e.g., mycosporine-like amino acids)(Huovinen et al. 2004). Whe<strong>the</strong>r algae from different latitudes exhibit a differential susceptibilityto UV radiation in <strong>the</strong> context <strong>of</strong> <strong>the</strong> HCS remains unclear <strong>and</strong> future work should give new insightsinto <strong>the</strong> ecophysiological strategies <strong>of</strong> macroalgal assemblages in scenarios <strong>of</strong> climate change.A brief history <strong>of</strong> exploitation <strong>of</strong> natural resources in <strong>the</strong> HCSFirst coastal settlersEvidence <strong>of</strong> coastline occupation <strong>of</strong>f Peru <strong>and</strong> Chile may date from as early as 11,000 yr ago(Llagostera 1979, Muñoz 1982, Báez et al. 1994, Keefer et al. 1998, S<strong>and</strong>weiss et al. 1998, Méndez2002, Méndez & Jackson 2004, Santoro et al. 2005). One <strong>of</strong> <strong>the</strong> first studies <strong>of</strong> <strong>the</strong> earliest humanhabitation along <strong>the</strong> coast <strong>of</strong> nor<strong>the</strong>rn-<strong>central</strong> Chile (Arica to Coquimbo) was carried out by JuniusBird in 1941 during excavations <strong>of</strong> shell middens. This author (Bird 1943, 1946) showed that <strong>the</strong>earliest evidence <strong>of</strong> human settlements on this coast went back to ~6000 yr before present (BP)<strong>and</strong> people used highly specialised artifacts with an efficient maritime adaptation. According toSantoro et al. (2005) evidence <strong>of</strong> <strong>the</strong> earliest inhabitants (~11,000 yr BP) is difficult to find sincemost prehistoric sites are now on drowned l<strong>and</strong>scapes. However, <strong>the</strong>re is clear evidence that coastalpopulations in nor<strong>the</strong>rn-<strong>central</strong> Chile used marine natural resources during <strong>the</strong> Holocene (Llagostera1979). It is thought that early fishermen dived in subtidal waters to collect molluscs <strong>and</strong> <strong>the</strong>y also277

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