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Dispersal of marine organisms in the Baltic Sea Per Jonsson Dept of Marine Ecology Tjärnö Marine Biological Laboratory University of Gothenburg “The marine ecosystem in changing climate”, SMHI October 16th, 2009 Dispersal of marine organisms •The Challenge: •How ? are marine populations connected through dispersal? ? ? ? ecological evolutionary time time Dispersal & connectivity affect: Fluctuations in population size Local extinction Invasion of non-native Evolution of local species adaptations Evolutionary rate & Management of exploited speciation species Design of Marine Protected Areas (MPA) Why is connectivity important when designing local recruitment ofMPAs? isolated MPAs reduce risk of local extinction in networks di sp er s al Many sedentary (or sessile) adults photo: Pia Pettersson photo: Nils Kautsky photo: Lars-Ove Loo Typical life cycle sessile sessile adult adult gametes gametes juvenile juvenile zygot zygot embryo embryo free-swimming free-swimming larva larva Marine dispersal is difficult to study •Most marine propagules (spores & larvae) are numerous, sub-mm, and drift with ocean circulation •Duration of planktonic dispersal: hours to weeks Marine dispersal is poorly understood Mean dispersal distance? Direction? Temporal and spatial variation in dispersal? How can we study connectivity? Our approach: Models based on oceanographic circulation Oceanographic model Multiple trajectories from each model grid Biological models Vertical migration & settling 0 -2 Depth (m) -4 -6 -8 -10 -12 -14 -16 -18 Poorly Poorly known known indeed! indeed! 23 21 19 15 17 Time (h) 13 11 9 7 5 3 1 -20 Model domain Mytilus edulis (trossulus) areas ≤12 m depth Sub-populations and the connectivity matrix From 1 2 3 4 5 To To 1 s e21 e31 e41 e51 sub -population sub-population 1 2 3 4 2 e12 s e32 e42 e52 3 e13 e23 s e43 e53 4 e14 e24 e34 s e54 5 e15 e25 e35 e45 s 5 The connectivity matrix of the shallow Baltic Sea 27 million elements Larval dispersal Longest dispersal: 380 km 6.E+07 6.E+07 21 days of dispers al 5.E+07 5.E+07 4.E+07 4.E+07 3.E+07 3.E+07 2.E+07 2.E+07 1.E+07 1.E+07 0.E+00 0.E+00 00 15 15 30 30 45 45 60 60 75 75 90 90 105 105 120 120 135 135 150 150 Dispersal Dispersal distance distance (km) (km) Can we use connectivity information to improve MPA design? Identify dispersal barriers Select networks of MPA that are internally connected Assess the connectivity of existing MPAs We suggest a new framework for analysis of connectivity Based on eigenvectors of the connectivity matrix 1 2 3 4 5 6 0. 0 3 0. 0 3 0. 0. 3 5 7 1 1 0 0 0 0 2 0 0 0 0 3 0 0 0 0 0 0 0 0 0 0 0 0 1 0 0 0 4 5 6 0. 5 0. 5 0 0 1 0 0 0 4 0 0 0. 0. 5 5 0. 0 5 7 0 0 0 0 0 define sources & sinks identify well-linked regions 5 2sink 3 7 source 6 Internally linked regions May indicate gene flow May indicate local populations Stratification criterion for MPAs Finding an ‘optimum’ MPA We propose that the optimum network network consists of the subset of areas having the largest product of dominant right- and left We define the optimum network as the eigenvectors subset of areas having the largest metapopulation size based on a simplistic population projection model Optimum network subset of 5000 km2 Optimum network: performance 10 Network population size optimum network 1 0.1 0.01 10 random networks 0.001 0.0001 0.00001 0 0 2500 200 5000 7500 10000 12500 15000 400 600 800 1000 MPA network size 2) MPA number (km 1200 Optimum network vs Natura 2000 populatio n size 18% of optimum network all areas optimum all areas N 2000 Will connectivity change with the •increasedclimate? precipitation •increased stratification •changing wind fields ocity fields for IPCC scenarios up to year 2 Predicted change in salinity Present 2070 RCAO-ECHAM4/A2 5 psu from Meier 2008, SMHI Conclusions Dispersal models based on ocean circulation models is a way forward Connectivity is presently not used when selecting MPAs Connectivity may significantly affect MPA performance Eigenvector analysis may be an easy way to link connectivity to MPA design Ongoing Formas project: “Larval dispersal and the design of marine reserve networks in Sweden” • Assess the importance of connectivity for MPA design • Include Skagerrak (+North Sea?) Vattenkikaren • Develop a tool to include connectivity as a criterion in design of MPA and no-take areas Problems & Challenges dispersal distance distance (km) (km) dispersal Larval Larval behaviour behaviour -- not not only only passive passive ‘particles’ ‘particles’ swim depth: larval larval duration duration (days) (days) Spread of invasive species Kattegatt Öresund Roslagen Gävle Åland Gulf of Finland Hanö Kvarken, SE Gulf of Riga Öland Kvarken, Fin Poland Thank you ! Collaborators: Kristofer Döös, Stockholm University Hanna Corell, Stockholm University Per Moksnes, University of Gothenburg Per Nilsson, University of Gothenburg David Kleinhans, University of Gothenburg Martin Nilsson Jacobi, Chalmers