12.07.2015 Views

the humboldt current system of northern and central chile - figema

the humboldt current system of northern and central chile - figema

the humboldt current system of northern and central chile - figema

SHOW MORE
SHOW LESS

You also want an ePaper? Increase the reach of your titles

YUMPU automatically turns print PDFs into web optimized ePapers that Google loves.

MARTIN THIEL ET AL.storms delivered larvae <strong>of</strong> several gastropod species to <strong>the</strong> shore (Marín & Moreno 2002, C.A.Moreno in a personal communication to S.A. Navarrete).Few studies have directly <strong>and</strong> simultaneously examined <strong>the</strong> distribution <strong>of</strong> larvae in <strong>the</strong> plankton,physical processes <strong>and</strong> settlement onshore in <strong>the</strong> HCS. Even fewer have examined larval behaviourunder field or laboratory conditions (Poulin et al. 2002a,b, Manríquez et al. 2004, Vargas et al.2006a).Patterns <strong>of</strong> recruitment <strong>and</strong> benthic communitiesSystematic studies <strong>of</strong> recruitment <strong>of</strong> species in <strong>the</strong> HCS have focused on (1) characterising spatial<strong>and</strong> temporal variation in <strong>the</strong> arrival <strong>of</strong> new individuals for intertidal <strong>and</strong> a few subtidal species(e.g., Jara & Moreno 1983, H<strong>of</strong>fmann & Santelices 1991, Stotz et al. 1991a, Camus & Lagos 1996,Martínez & Navarrete 2002); (2) relating <strong>the</strong>se patterns with large-scale oceanographic anomalies,such as El Niño events (e.g., Moreno et al. 1998, Navarrete et al. 2002); (3) examining <strong>the</strong> effects<strong>of</strong> recruitment variability on population dynamics <strong>and</strong> recovery <strong>of</strong> local populations from physical,biological or human-induced disturbance (e.g., Santelices & Ojeda 1984, Moreno et al. 1993b,Duarte et al. 1996, Alvarado et al. 2001); (4) determining <strong>the</strong> consequences <strong>of</strong> recruitment variationon <strong>the</strong> nature <strong>and</strong> intensity <strong>of</strong> species interactions in <strong>the</strong> adult habitat (e.g., Navarrete & Castilla1990, Moreno 1995, Navarrete et al. 2005, Wieters 2005); <strong>and</strong> (5) characterising <strong>the</strong> effects on <strong>the</strong>processes that regulate <strong>the</strong> dynamics <strong>of</strong> entire intertidal communities over large spatial scales(Navarrete et al. 2005).The far-reaching ramifications <strong>of</strong> persistent variation in recruitment have been most amplydemonstrated in recent studies that quantify patterns <strong>of</strong> recruitment over large temporal (years) <strong>and</strong>spatial (tens to hundreds <strong>of</strong> kilometres) scales. These studies are starting to shed light on, <strong>and</strong> findre<strong>current</strong> patterns in, <strong>the</strong> causes <strong>of</strong> <strong>the</strong> typically large, baffling <strong>and</strong> usually ‘unpredictable’ variationin coastal eco<strong>system</strong>s. Studies along <strong>the</strong> California coast have found large-scale regularities inpatterns <strong>of</strong> recruitment <strong>of</strong> sessile species that can help reconcile odd experimental results (Mengeet al. 1994, Connolly et al. 2001, Menge et al. 2003). Studies in <strong>the</strong> HCS conducted by Navarreteet al. (2002, 2005) have evaluated <strong>the</strong> effects <strong>of</strong> variation in wind-driven upwelling on communityregulation along 900 km <strong>of</strong> coastline between 29°S <strong>and</strong> 35°S during 72 months. Sharp discontinuitiesin upwelling regimes around 30–32°S produced abrupt <strong>and</strong> persistent breaks in <strong>the</strong> dynamics<strong>of</strong> benthic <strong>and</strong> pelagic communities over hundreds <strong>of</strong> kilometres (regional scales) (Figure 15A,B).Rates <strong>of</strong> mussel <strong>and</strong> barnacle recruitment changed sharply at 32°S, determining a geographic breakin adult abundance <strong>of</strong> <strong>the</strong>se competitively dominant species. Analyses <strong>of</strong> satellite images alsocorroborate <strong>the</strong> existence <strong>of</strong> regional-scale discontinuities in dynamics <strong>and</strong> concentration <strong>of</strong> <strong>of</strong>fshoresurface chl-a that had been previously described at coarser resolution (Thomas 1999, Thomas et al.2001b). Intertidal field experiments showed that <strong>the</strong> paradigm <strong>of</strong> top-down control <strong>of</strong> intertidalbenthic communities (Castilla & Durán 1985, Paine et al. 1985, Castilla 1999, Navarrete & Castilla2003) holds only south <strong>of</strong> this geographic discontinuity. To <strong>the</strong> north, populations seem recruitmentlimited, <strong>and</strong> predators have negligible effects, despite attaining similarly high abundances. Thus,geographically discontinuous oceanographic regimes set bounds to <strong>the</strong> strength <strong>of</strong> species interactions<strong>and</strong> define distinct regions for <strong>the</strong> design <strong>and</strong> implementation <strong>of</strong> sustainable management<strong>and</strong> conservation policies along <strong>the</strong> HCS. Fur<strong>the</strong>r ecological studies using molecular markers areneeded to define <strong>the</strong> consequences <strong>of</strong> this variation for <strong>the</strong> genetic population structure <strong>of</strong> mussels<strong>and</strong> barnacles, as well as for o<strong>the</strong>r components <strong>of</strong> intertidal communities, many <strong>of</strong> which do notexperience such a discontinuity in recruitment, despite having similar life histories <strong>and</strong> generalbiology (Figure 15C,D).250

Hooray! Your file is uploaded and ready to be published.

Saved successfully!

Ooh no, something went wrong!