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The 47th
European Marine Biology Symposium, Arendal, Norway, 3–7 September 2012 alexander.juterbock@uin.no
Climate change impact on seaweed meadow distribution in the North Atlantic
Jueterbock A.1
, Tyberghein L.2
, Verbruggen H. 3
, Coyer J.A.4
, Olsen J.L.5
, Hoarau G.1
1 Faculty of Biosciences and Aquaculture, University of Nordland, Bodø, Norway
2 Phycology Research Group, University of Ghent, Ghent, Belgium
3 School of Botany, University of Melbourne, Victoria, Australia
4 Shoals Marine Laboratory, Cornell University, Portsmouth, NH, USA
5 Department of Marine Benthic Ecology and Evolution, University of Groningen, Groningen, The Netherlands
Background Climate change affects seaweed meadows on temperate rocky shores
1999
2010
Seaweeds mediate the climate warming impact
on North Atlantic rocky shores
Under predicted climate change, the future state
of the rocky shore community depends on how
marine intertidal key species respond. Sea-
weeds are key elements of temperate rocky in-
tertidal communities and provide an excellent sys-
tem in which to investigate the impact of climate
change since their distributional boundaries
are commonly correlated with SST isotherms.
Ongoing poleward shift
Evidence arose over the last
decade that climate change
causes a global poleward shift of
temperate seaweed species.
Research questions
1. Areas of biggest change?
2. Coherent shift of entire
temperate flora?
3. Can seaweeds trace the
predicted shift?
90% abundance de-
cline in Fucus serratus
Methods Ecological niche modeling
Occurrence records
+
Environmental layers
2000
+
Climate predictions
until 2200
Salinity (PSU)
Minimum surface air temperature (◦
C)
Mean sea surface temperature (◦
C)
Predicting future seaweed distribution
Three of the most abundant and characteris-
tic macroalgae of North Atlantic shores are Fu-
cus serratus, Fucus vesiculosus and Ascophyllum
nodosum. We estimated their ecological niches
based on their geographical occurrence and the
environmental conditions at these locations (from
the Bio-ORACLE database [4]) using the program
MAXENT [3]. Projections of the future state of these
conditions were then compiled with the R package
’raster’ [2] from three IPCC climate change projec-
tions (B1, A1B and A2) and the UKMO-HadCM3
model [1] to predict suitable seaweed habitats in
2100 and 2200.
Results Arctic gain and southern retreat
Habitat suitability changes under the
intermediate climate change scenario A1B
Northward shift
Already in 2100,
arctic shores in
Canada, Greenland
and Spitsbergen
are predicted to
become suitable for
the temperate sea-
weeds, but shores
south of Britain and
Newfoundland are
indicated to lose
at least two of the
three focal species
until 2200.
West Atlantic East Atlantic
Predicted change of latitudinal distribution boundaries for the three al-
gal species over the next two centuries. Bars of one standard error indicate
the variation that is due to the different IPCC scenarios and different thresh-
old rules that discriminate suitable from non-suitable habitat. F. serratus, F.
vesiculosus and A. nodosum were predicted to lose 5.0◦
, 7.0◦
and 3.6◦
lat-
itude in the NW- and 12.0◦
, 9.1◦
and 7.3◦
latitude in the NE-Atlantic and to
gain 14.9◦
, 5.7◦
and 9.8◦
latitude in the NW- and 8.3◦
, 9.6◦
and 8.5◦
latitude
in the NE-Atlantic, respectively.
References
[1] Gordon, C.; Cooper, C.; Senior, C.A.; Banks, H.; Gregory, J.M.; Johns, T.C.;Mitchell, J.F.B. & Wood, R.A. (2000): The simulation of SST, sea ice extents and ocean heat transports in a version of
the Hadley Centre coupled model without flux adjustments. Climate Dynamics 16(2):147–168
[2] Hijmans, R.J. & van Etten, J. (2011): Package ’raster’: Geographic analysis and modeling with raster data
[3] Phillips, S.J.; Anderson, R.P. & Schapire, R.E. (2006): Maximum entropy modeling of species geographic distributions. Ecol. Model. 190(3–4):231–259
[4] Tyberghein, L.; Verbruggen, H.; Pauly, K.; Troupin, C.; Mineur, F. & De Clerck, O. (2011): Bio-ORACLE: a global environmental dataset for marine species distribution modelling. Global Ecol.
Biogeogr. 21(2):272–281
Conclusions
1. Biggest changes are expected in phytogeographic transition zones like the southern arctic and temperate provinces.
2. The temperate marine flora is likely to restructure into a nonanalogous hybrid community since its component species shift incoherently.
3. Human shipping could induce a rapid invasion of temperate seaweeds in the Arctic despite their low intrinsic dispersal potential.

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Climate change impact on seaweed meadow distribution in the North Atlantic rocky intertidal

  • 1. The 47th European Marine Biology Symposium, Arendal, Norway, 3–7 September 2012 alexander.juterbock@uin.no Climate change impact on seaweed meadow distribution in the North Atlantic Jueterbock A.1 , Tyberghein L.2 , Verbruggen H. 3 , Coyer J.A.4 , Olsen J.L.5 , Hoarau G.1 1 Faculty of Biosciences and Aquaculture, University of Nordland, Bodø, Norway 2 Phycology Research Group, University of Ghent, Ghent, Belgium 3 School of Botany, University of Melbourne, Victoria, Australia 4 Shoals Marine Laboratory, Cornell University, Portsmouth, NH, USA 5 Department of Marine Benthic Ecology and Evolution, University of Groningen, Groningen, The Netherlands Background Climate change affects seaweed meadows on temperate rocky shores 1999 2010 Seaweeds mediate the climate warming impact on North Atlantic rocky shores Under predicted climate change, the future state of the rocky shore community depends on how marine intertidal key species respond. Sea- weeds are key elements of temperate rocky in- tertidal communities and provide an excellent sys- tem in which to investigate the impact of climate change since their distributional boundaries are commonly correlated with SST isotherms. Ongoing poleward shift Evidence arose over the last decade that climate change causes a global poleward shift of temperate seaweed species. Research questions 1. Areas of biggest change? 2. Coherent shift of entire temperate flora? 3. Can seaweeds trace the predicted shift? 90% abundance de- cline in Fucus serratus Methods Ecological niche modeling Occurrence records + Environmental layers 2000 + Climate predictions until 2200 Salinity (PSU) Minimum surface air temperature (◦ C) Mean sea surface temperature (◦ C) Predicting future seaweed distribution Three of the most abundant and characteris- tic macroalgae of North Atlantic shores are Fu- cus serratus, Fucus vesiculosus and Ascophyllum nodosum. We estimated their ecological niches based on their geographical occurrence and the environmental conditions at these locations (from the Bio-ORACLE database [4]) using the program MAXENT [3]. Projections of the future state of these conditions were then compiled with the R package ’raster’ [2] from three IPCC climate change projec- tions (B1, A1B and A2) and the UKMO-HadCM3 model [1] to predict suitable seaweed habitats in 2100 and 2200. Results Arctic gain and southern retreat Habitat suitability changes under the intermediate climate change scenario A1B Northward shift Already in 2100, arctic shores in Canada, Greenland and Spitsbergen are predicted to become suitable for the temperate sea- weeds, but shores south of Britain and Newfoundland are indicated to lose at least two of the three focal species until 2200. West Atlantic East Atlantic Predicted change of latitudinal distribution boundaries for the three al- gal species over the next two centuries. Bars of one standard error indicate the variation that is due to the different IPCC scenarios and different thresh- old rules that discriminate suitable from non-suitable habitat. F. serratus, F. vesiculosus and A. nodosum were predicted to lose 5.0◦ , 7.0◦ and 3.6◦ lat- itude in the NW- and 12.0◦ , 9.1◦ and 7.3◦ latitude in the NE-Atlantic and to gain 14.9◦ , 5.7◦ and 9.8◦ latitude in the NW- and 8.3◦ , 9.6◦ and 8.5◦ latitude in the NE-Atlantic, respectively. References [1] Gordon, C.; Cooper, C.; Senior, C.A.; Banks, H.; Gregory, J.M.; Johns, T.C.;Mitchell, J.F.B. & Wood, R.A. (2000): The simulation of SST, sea ice extents and ocean heat transports in a version of the Hadley Centre coupled model without flux adjustments. Climate Dynamics 16(2):147–168 [2] Hijmans, R.J. & van Etten, J. (2011): Package ’raster’: Geographic analysis and modeling with raster data [3] Phillips, S.J.; Anderson, R.P. & Schapire, R.E. (2006): Maximum entropy modeling of species geographic distributions. Ecol. Model. 190(3–4):231–259 [4] Tyberghein, L.; Verbruggen, H.; Pauly, K.; Troupin, C.; Mineur, F. & De Clerck, O. (2011): Bio-ORACLE: a global environmental dataset for marine species distribution modelling. Global Ecol. Biogeogr. 21(2):272–281 Conclusions 1. Biggest changes are expected in phytogeographic transition zones like the southern arctic and temperate provinces. 2. The temperate marine flora is likely to restructure into a nonanalogous hybrid community since its component species shift incoherently. 3. Human shipping could induce a rapid invasion of temperate seaweeds in the Arctic despite their low intrinsic dispersal potential.