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Variation that can be expected when using particle tracking models in connectivity studies
Hufnagl, M.; Payne, M.; Lacroix, G.; Bolle, L.J.; Daewel, U.; Dickey-Collas, M.; Gerkema, T.; Huret, M.; Janssen, F.; Kreus, M.; Pätsch, J.; Pohlmann, T.; Ruardij, P.; Schrum, C.; Skogen, M.D.; Tiessen, M.C.H.; Petitgas, P.; van Beek, J.K.L.; van der Veer, H.W.; Callies, U. (2017). Variation that can be expected when using particle tracking models in connectivity studies. J. Sea Res. 127: 133-149. https://dx.doi.org/10.1016/j.seares.2017.04.009
In: Journal of Sea Research. Elsevier/Netherlands Institute for Sea Research: Amsterdam; Den Burg. ISSN 1385-1101; e-ISSN 1873-1414
Peer reviewed article  
Available in  Authors 
Keyword
    Marine/Coastal
Author keywords
    Ocean circulation; Lagrangian approach; Variability; Marine protectedareas; Renewable energy; Wind park; Model intercomparison; Ensemble
Authors  Top 
  • Hufnagl, M.
  • Payne, M.
  • Lacroix, G.
  • Bolle, L.J.
  • Daewel, U.
  • Dickey-Collas, M.
  • Gerkema, T.
  • Huret, M.
  • Janssen, F.
  • Kreus, M.
  • Pätsch, J.
  • Pohlmann, T.
  • Ruardij, P.
  • Schrum, C.
  • Skogen, M.D.
  • Tiessen, M.C.H.
  • Petitgas, P.
  • van Beek, J.K.L.
  • van der Veer, H.W.
  • Callies, U.
Abstract
    Hydrodynamic Ocean Circulation Models and Lagrangian particle tracking models are valuable tools e.g. in coastal ecology to identify the connectivity between offshore spawning and coastal nursery areas of commercially important fish, for risk assessment and more for defining or evaluating marine protected areas. Most studies are based on only one model and do not provide levels of uncertainty. Here this uncertainty was addressed by applying a suite of 11 North Sea models to test what variability can be expected concerning connectivity. Different notional test cases were calculated related to three important and well-studied North Sea fish species: herring (Clupea harengus), and the flatfishes sole (Solea solea) and plaice (Pleuronectes platessa). For sole and plaice we determined which fraction of particles released in the respective spawning areas would reach a coastal marine protected area. For herring we determined the fraction located in a wind park after a predefined time span. As temperature is more and more a focus especially in biological and global change studies, furthermore inter-model variability in temperatures experienced by the virtual particles was determined. The main focus was on the transport variability originating from the physical models and thus biological behavior was not included. Depending on the scenario, median experienced temperatures differed by 3 °C between years. The range between the different models in one year was comparable to this temperature range observed between modelled years. Connectivity between flatfish spawning areas and the coastal protected area was highly dependent on the release location and spawning time. No particles released in the English Channel in the sole scenario reached the protected area while up to 20% of the particles released in the plaice scenario did. Interannual trends in transport directions and connectivity rates were comparable between models but absolute values displayed high variations. Most models showed systematic biases during all years in comparison to the ensemble median, indicating that in general interannual variation was represented but absolute values varied. In conclusion: variability between models is generally high and management decisions or scientific analysis using absolute values from only one single model might be biased and results or conclusions drawn from such studies need to be treated with caution. We further concluded that more true validation data for particle modelling are required.
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