Difference between revisions of "Effects of global climate change on European marine biodiversity"

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Global warming has a range of effects on marine systems. The effects may be related to changing water temperatures, changing water circulation or changing habitat; as a consequence of these changes,  altered pathways within biogeochemical cycles and food webs are detected as well. In the first case, the biological responses and impacts result from the physical effects.<ref name="Phillipart"> Phillipart C.J.M. (ed.) (2007). Impacts of climate change on the European marine and coastal environment: ecosystems approach.'' European Science Foundation, Marine Board: Strasbourg, France.'' 82pp.</ref>
 
  
Even without human-induced climate change, [[Natural variability in Coastal Ecosystems|the biodiversity and biogeography of species is continuously changing]] (seasonal and yearly changes). Consequently, long term monitoring is necessary in order to evaluate these processes. The marine systems however may become more dynamic and variable due to climate change.<ref name="Phillipart"> Phillipart C.J.M. (ed.) (2007). Impacts of climate change on the European marine and coastal environment: ecosystems approach.'' European Science Foundation, Marine Board: Strasbourg, France.'' 82pp.</ref>
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This article discusses global warming and the range of effects on marine systems.
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The effects may be related to changing water temperatures, changing water circulation or changing habitat; as a consequence of these changes,  altered pathways within biogeochemical cycles and food webs are detected as well. In the first case, the biological responses and impacts result from the physical effects.<ref name="Phillipart"> Phillipart C.J.M. (ed.) (2007). Impacts of climate change on the European marine and coastal environment: ecosystems approach.'' European Science Foundation, Marine Board: Strasbourg, France.'' 82pp.</ref>
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Even without human-induced [[climate change]], [[Natural variability and change in coastal ecosystems|the biodiversity and biogeography of species is continuously changing]] (seasonal and yearly changes). Consequently, long term monitoring is necessary in order to evaluate these processes. The marine systems however may become more dynamic and variable due to climate change.<ref name="Phillipart"> Phillipart C.J.M. (ed.) (2007). Impacts of climate change on the European marine and coastal environment: ecosystems approach.'' European Science Foundation, Marine Board: Strasbourg, France.'' 82pp.</ref>
 
   
 
   
Europe may be less threatened by sea-level rise than many developing country regions. However, coastal ecosystems do appear to be threatened, especially enclosed seas such as the Baltic, the Mediterranean and the Black Sea. These seas have only small and primarily east-west orientated movement corridors, which may restrict northward displacement of organisms in these areas.<ref name="Nicholls"> Nicholls, R.J.; Klein,R.J.T. (2005). Climate change and coastal management on Europe's coast, '''in''': Vermaat, J.E. ''et al.'' (Ed.) (2005). Managing European coasts: past, present and future. pp. 199-226.</ref>
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Coastal ecosystems of the enclosed seas such as the [[Baltic Sea|Baltic]], the [[Mediterranean Sea and Region, including Adriatic Sea|Mediterranean]] and the [[Black Sea]] are most threatened bu climate change. These seas have only small and primarily east-west orientated movement corridors, which may restrict northward displacement of organisms in these areas.<ref name="Nicholls"> Nicholls, R.J.; Klein,R.J.T. (2005). Climate change and coastal management on Europe's coast, '''in''': Vermaat, J.E. ''et al.'' (Ed.) (2005). Managing European coasts: past, present and future. pp. 199-226.</ref>
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==Effects on primary production==
 
==Effects on primary production==
 
   
 
   
Higher temperatures and enhanced [[stratification]] could affect the productivity of [[phytoplankton]]. A number of models predict an increase in global [[Primary production|primary production]] of between 1% and 8% by 2050, when compared to pre-industrial times.<ref name="Sarmiento"> Sarmiento, J.L.; Slater, R.; Barber, R.; Bopp, L.; Doney, S.C.; Hirst, A.C., Kleypas, J.; Matear, R.; Mikolajewicz, U.; Monfray, P.; Soldatov, V.; Spall, S.A.; Stouffer, R. (2004). Response of ocean ecosystems to climate warming. ''Glob Biogeoch Cycles'' 18,3. '''in''': Philippart, C.J.M. (Ed.). (2007). Impacts of climate change on the European marine and coastal environment: ecosystems approach. ''ESF Marine Board Position Paper''. European Science Foundation, Marine Board: Strasbourg, France. 82 pp.</ref>  
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Higher temperatures and enhanced [[stratification]] could affect the productivity of [[phytoplankton]]. A number of models predict an increase in global [[Primary production|primary production]] of between 1% and 8% by 2050, when compared to pre-industrial times.<ref name="Sarmiento"> Sarmiento, J.L.; Slater, R.; Barber, R.; Bopp, L.; Doney, S.C.; Hirst, A.C., Kleypas, J.; Matear, R.; Mikolajewicz, U.; Monfray, P.; Soldatov, V.; Spall, S.A.; Stouffer, R. (2004). Response of ocean ecosystems to climate warming. ''Glob Biogeoch Cycles'' 18,3. '''cit. in''': Philippart, C.J.M. (Ed.). (2007). Impacts of climate change on the European marine and coastal environment: ecosystems approach. ''ESF Marine Board Position Paper''. European Science Foundation, Marine Board: Strasbourg, France. 82 pp.</ref>  
  
Because phytoplankton is an important basis of the marine food web, any change in the timing, abundance or species composition of the phytoplankton will have an effect on the whole food web.<ref name="Phillipart"> Phillipart C.J.M. (ed.) (2007). Impacts of climate change on the European marine and coastal environment: ecosystems approach.'' European Science Foundation, Marine Board: Strasbourg, France.'' 82pp.</ref>
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Because phytoplankton is an important basis of the marine [[food web]], any change in the timing, abundance or species composition of the phytoplankton will have an effect on the whole food web.<ref name="Phillipart"> Phillipart C.J.M. (ed.) (2007). Impacts of climate change on the European marine and coastal environment: ecosystems approach.'' European Science Foundation, Marine Board: Strasbourg, France.'' 82pp.</ref>
  
 
==Effects on the recruitment process==
 
==Effects on the recruitment process==
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===Example: cod recruitment in the North Sea===
 
===Example: cod recruitment in the North Sea===
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The Atlantic cod (''Gadus morhua'') recruitment in the North Sea, in the past 40 years, was influenced by changes at the base of the food web (bottom-up-control), induced by the rise of temperature. Cod recruitment decreased from the mid-1980s, coincident with unfavorable changes in the plankton ecosystem.<ref name="Beaugrand"> Beaugrand, G.; Brander, K.M.; Lindley, J.A.; Souissi, S.; Reid, P.C. (2003). Plankton effect on cod recruitment in the North Sea.''Nature (Lond.) 426(6967)'': 661-664.</ref> (Fig.1)
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The Atlantic cod (''Gadus morhua'') recruitment in the [[North Sea]], in the past 40 years, was influenced by changes at the base of the food web (bottom-up-control), induced by the rise of temperature. Cod recruitment decreased from the mid-1980s, coincident with unfavorable changes in the plankton ecosystem.<ref name="Beaugrand"> Beaugrand, G.; Brander, K.M.; Lindley, J.A.; Souissi, S.; Reid, P.C. (2003). Plankton effect on cod recruitment in the North Sea.''Nature (Lond.) 426(6967)'': 661-664.</ref>
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[[Image:Atlantic cod.jpg|right|300px|Atlantic cod ''Gadus morhua'' SOURCE: www.fishbase.org |frame]]
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[[Image:cod recruitment.jpg|centre|300px|Long-term changes (1958-1999) in the plankton index (in black), and long-term changes (1959-2000) in cod recruitment (in red, decimal logarithm).(Biological parameters for the diet and growth of cod larvae and juveniles: total calanoid copepods (qualitative indicator of food for larval cod), the mean size of calanoid copepods (qualitative indicator of food) and the abundance of two dominant congeneric species (Calanus finmarchicus and C. helgolandicus). Reprinted by permission from Macmillan Publishers Ltd: [NATURE] (Beaugrand, G.; Brander, K.M.; Lindley, J.A.; Souissi, S.; Reid, P.C. (2003). Plankton effect on cod recruitment in the North Sea. ''Nature (Lond.) 426(6967''): 661-664.), copyright (2003)|frame]]
  
 
==Effects on the [[biogeography]]==  
 
==Effects on the [[biogeography]]==  
  
The species movement in a warming area is towards the poles in general. Since global warming accelerated in the late 1980s, pole ward advances of southern species and retreats of northern species have been recorded in [[zooplankton]], fish and benthic species.<ref name="Brander"> Brander, K.; Blom, G.; Borges, M.F.; Erzini, K.; Henderson, G.; MacKenszie, B.R.; Mendes, H.; Ribeiro, J.; Santos, A.M.P.; Toresen, T. (2003). Changes in fish distribution in the eastern North Atlantic: Are we seeing a coherent response to changing temperature? ''ICES Mar Sci Symp'' 219: 261-270. '''in''': Philippart, C.J.M. (Ed.). (2007). Impacts of climate change on the European marine and coastal environment: ecosystems approach. ''ESF Marine Board Position Paper''. European Science Foundation, Marine Board: Strasbourg, France. 82 pp.</ref> .<ref name="Southward2005"> Southward, A.J.; Hawkins, S.J.; Burrowa, M.T. (1995). Seventy years` observations of changes in distribution and abundance of zooplankton and intertidal organisms in the western English Channel in relation to rising sea temperature. ''J Therm Biol'' 20: 127-155. '''in''': Philippart, C.J.M. (Ed.). (2007). Impacts of climate change on the European marine and coastal environment: ecosystems approach. ''ESF Marine Board Position Paper''. European Science Foundation, Marine Board: Strasbourg, France. 82 pp.</ref>  
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The species movement in a warming area is towards the poles in general. Since global warming accelerated in the late 1980s, pole ward advances of southern species and retreats of northern species have been recorded in [[zooplankton]], fish and benthic species.<ref name="Brander"> Brander, K.; Blom, G.; Borges, M.F.; Erzini, K.; Henderson, G.; MacKenszie, B.R.; Mendes, H.; Ribeiro, J.; Santos, A.M.P.; Toresen, T. (2003). Changes in fish distribution in the eastern North Atlantic: Are we seeing a coherent response to changing temperature? ''ICES Mar Sci Symp'' 219: 261-270. '''cit. in''': Philippart, C.J.M. (Ed.). (2007). Impacts of climate change on the European marine and coastal environment: ecosystems approach. ''ESF Marine Board Position Paper''. European Science Foundation, Marine Board: Strasbourg, France. 82 pp.</ref> .<ref name="Southward2005"> Southward, A.J.; Langmead, O.; Hardman-Mountford, N.J.; Aiken, J.; Boalch, G.T.; Dando, P.R.; Genner, M.J.; Joint, I.; Kendall, M; Halliday, N.C.; Harris, R.P.; Leaper, R.; Mieszkowska, N.; Pingree, R.D.; Richardson, A.J.; Sims, D.W.; Smith, T.; Walne, A.W.; Hawkins, S.J. (2005). Long term oceanographic and ecological research in the western English Channel. ''Adv Mar Biol'' 47: 1-105 '''cit. in''': Philippart, C.J.M. (Ed.). (2007). Impacts of climate change on the European marine and coastal environment: ecosystems approach. ''ESF Marine Board Position Paper''. European Science Foundation, Marine Board: Strasbourg, France. 82 pp.</ref>  
  
 
The species distribution is not always northwards. For example when the stock of the main prey of the harp seals in the Barents Sea collapsed, these seals migrated southwards along the coast of Norway and into the North Sea in search of food.<ref name="Phillipart"> Phillipart C.J.M. (ed.) (2007). Impacts of climate change on the European marine and coastal environment: ecosystems approach.'' European Science Foundation, Marine Board: Strasbourg, France.'' 82pp.</ref>
 
The species distribution is not always northwards. For example when the stock of the main prey of the harp seals in the Barents Sea collapsed, these seals migrated southwards along the coast of Norway and into the North Sea in search of food.<ref name="Phillipart"> Phillipart C.J.M. (ed.) (2007). Impacts of climate change on the European marine and coastal environment: ecosystems approach.'' European Science Foundation, Marine Board: Strasbourg, France.'' 82pp.</ref>
  
 
===Example: Study of barnacles in the Celtic-Biscay shelf===
 
===Example: Study of barnacles in the Celtic-Biscay shelf===
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[[Image:barnacles.jpg|right|300px|Long-term changes in ''Semibalanus balanoides'' and ''Chthamalus'' spp. for several shores at different submersion levels (HWN: High Water Neap; MTL: Mean Tidal Low; LWN: Low Water Neap) on the south coast of Devon and Cornwall. SOURCE: © Southward 1995<ref name="Southward1995"> Southward, A.J.; Hawkins, S.J.; Burrowa, M.T. (1995). Seventy years` observations of changes in distribution and abundance of zooplankton and intertidal organisms in the western English Channel in relation to rising sea temperature. J'' Therm Biol'' 20: 127-155. '''cit. in''': Philippart, C.J.M. (Ed.). (2007). Impacts of climate change on the European marine and coastal environment: ecosystems approach. ''ESF Marine Board Position Paper''. European Science Foundation, Marine Board: Strasbourg, France. 82 pp.</ref>|frame]]
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The Celtic-Biscay shelf was liable to warming in the 1930; in the 1960 there was a switch back to colder. Changes in species assemblages were described on rocky shores, using barnacles as a sensitive indicator of wider changes in marine life.<ref name="Southward1995"> .Southward, A.J.; Hawkins, S.J.; Burrowa, M.T. (1995). Seventy years` observations of changes in distribution and abundance of zooplankton and intertidal organisms in the western English Channel in relation to rising sea temperature. J'' Therm Biol'' 20: 127-155. '''cit. in''': Philippart, C.J.M. (Ed.). (2007). Impacts of climate change on the European marine and coastal environment: ecosystems approach. ''ESF Marine Board Position Paper''. European Science Foundation, Marine Board: Strasbourg, France. 82 pp.</ref> <ref name="Southward2005"> Southward, A.J.; Langmead, O.; Hardman-Mountford, N.J.; Aiken, J.; Boalch, G.T.; Dando, P.R.; Genner, M.J.; Joint, I.; Kendall, M; Halliday, N.C.; Harris, R.P.; Leaper, R.; Mieszkowska, N.; Pingree, R.D.; Richardson, A.J.; Sims, D.W.; Smith, T.; Walne, A.W.; Hawkins, S.J. (2005). Long term oceanographic and ecological research in the western English Channel. ''Adv Mar Biol'' 47: 1-105 '''in''': Philippart, C.J.M. (Ed.). (2007). Impacts of climate change on the European marine and coastal environment: ecosystems approach. ''ESF Marine Board Position Paper''. European Science Foundation, Marine Board: Strasbourg, France. 82 pp.</ref> These showed switches between warm water barnacles in the 1950s (''Chthamalus'' spp.) to greater dominance by the cold water barnacle ''Semibalanus balanoides'' in the 1960s and 1970s. On rocky shores warm water barnacles now exceed the levels found in the 1950s.<ref name="Phillipart"> Phillipart C.J.M. (ed.) (2007). Impacts of climate change on the European marine and coastal environment: ecosystems approach.'' European Science Foundation, Marine Board: Strasbourg, France.'' 82pp.</ref>
  
The Celtic-Biscay shelf was liable to warming in the 1930; in the 1960 there was a switch back to colder. Changes in species assemblages were described on rocky shores, using barnacles as a sensitive indicator of wider changes in marine life. (Southward et al. 1995, 2005). These showed switches between warm water barnacles in the 1950s (''Chthamalus'' spp.) to greater dominance by the cold water barnacle ''Semibalanus balanoides'' in the 1960s and 1970s. On rocky shores warm water barnacles now exceed the levels found in the 1950s.<ref name="Phillipart"> Phillipart C.J.M. (ed.) (2007). Impacts of climate change on the European marine and coastal environment: ecosystems approach.'' European Science Foundation, Marine Board: Strasbourg, France.'' 82pp.</ref> (Fig.2)
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There are also examples from the [[Effects of climate change on the North Sea and Baltic Sea|North Sea and the Baltic Sea]].
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==Effects on the phenological relationships and community structure==
 
==Effects on the phenological relationships and community structure==
  
 
The response to climate changes differs between the species, inducing a decoupling of [[Phenology|phenological]] relationships (relative timing of life cycle events). The decoupling may affect the community structure and food webs by altering the interactions between a species and its competitors, mutualists, predators, prey or pathogens.  
 
The response to climate changes differs between the species, inducing a decoupling of [[Phenology|phenological]] relationships (relative timing of life cycle events). The decoupling may affect the community structure and food webs by altering the interactions between a species and its competitors, mutualists, predators, prey or pathogens.  
For example, in the case of seabirds, chick diet composition during development is likely to be an important mechanistic link between climate variability and the observed decline in seabird populations (Kitaysky et al. 2005 cit in 1).<ref name="Phillipart"> Phillipart C.J.M. (ed.) (2007). Impacts of climate change on the European marine and coastal environment: ecosystems approach.'' European Science Foundation, Marine Board: Strasbourg, France.'' 82pp.</ref>
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For example, in the case of seabirds, chick diet composition during development is likely to be an important mechanistic link between climate variability and the observed decline in seabird populations.<ref name="Kitaysky"> Kitaysky, A.S.; Kitaiskaia, E.V.; Piatt, J.F.; Wingfield, J.C. (2005). A mechanistic link between chick diet and decline in seabirds? ''Proc Biol Sci Proc R Soc B'' 273:445-450. '''cit. in''': Phillipart C.J.M. (ed.) (2007). Impacts of climate change on the European marine and coastal environment: ecosystems approach.''ESF Marine Board Position Paper''. European Science Foundation, Marine Board: Strasbourg, France. 82 pp.</ref>
  
 
A study in Kongsfjorden (79 °N) concluded that changing temperatures have a direct and very immediate influence on the species composition of plankton as well as on the biodiversity. The response of benthic organisms to rising temperature is slower and less drastic compared with planktonic organisms. Planktonic organisms may be a better indicator of global warming-driven changes than the benthic organisms. However benthic fauna is a good indicator of slow changes, especially when observed over a long period of time.<ref name="Kedra"> Kedra, M.; Walkusz, W. (2006). Global warming-driven biodiversity change: pelagic versus benthic domain [Arctic 79°N case study]'' MarBEF Newsletter'' 5: 23-24.</ref>
 
A study in Kongsfjorden (79 °N) concluded that changing temperatures have a direct and very immediate influence on the species composition of plankton as well as on the biodiversity. The response of benthic organisms to rising temperature is slower and less drastic compared with planktonic organisms. Planktonic organisms may be a better indicator of global warming-driven changes than the benthic organisms. However benthic fauna is a good indicator of slow changes, especially when observed over a long period of time.<ref name="Kedra"> Kedra, M.; Walkusz, W. (2006). Global warming-driven biodiversity change: pelagic versus benthic domain [Arctic 79°N case study]'' MarBEF Newsletter'' 5: 23-24.</ref>
  
 
==Effects on the establishment of invasive species==
 
==Effects on the establishment of invasive species==
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[[Image:Crassostrea gigas.jpg|right|300px| Pacific oyster ''Crassostrea gigas''  SOURCE: www.spirula.nl|frame]]
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The establishment of non-indigenous species can be accelerated by rapid warming. For example, the recent warming has accelerated the adaptation of the Pacific oyster (''Crassostrea gigas'') on the local circumstances in the Netherlands and the UK.<ref name="Essink"> Essink, K.; Dettmann, C.; Farke, H.; Laursen, K.; LuerBen, G.; Marencic, H.; Wiersinga, W. (Eds). Wadden Sea Quality Status Report 2004. ''Wadden Sea Ecosystems'' 19-2005, 155-161pp. '''cit. in''': Phillipart C.J.M. (ed.) (2007). Impacts of climate change on the European marine and coastal environment: ecosystems approach.''ESF Marine Board Position Paper''. European Science Foundation, Marine Board: Strasbourg, France. 82 pp.</ref>
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The establishment of non-indigenous species can be accelerated by rapid warming. For example, the recent warming has accelerated the adaptation of the Pacific oyster (''Crassostrea gigas'') on the local circumstances in the Netherlands and the UK (Reise ''et al.'' 2004 cit. in 1).
 
  
 
==Effects on biogeochemical cycles==
 
==Effects on biogeochemical cycles==
  
In the past 200 years the oceans have absorbed approximately half of the CO<sub>2</sub>  produced by fossil fuel burning and cement production. Calculations indicate that this uptake of CO<sub>2</sub> has led to a reduction of the pH of surface seawater ([[Acidification|acidification]]) of 0.1 units; this is an equivalent to a 30% increase in the concentration of hydrogen ions. If the CO<sub>2</sub> emissions from human activities rise on current trends then the average pH of the oceans could fall by 0.5 units by the year 2100.
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In the past 200 years the oceans have absorbed approximately half of the CO<sub>2</sub>  produced by fossil fuel burning and cement production. Calculations indicate that this uptake of CO<sub>2</sub> has led to a reduction of the pH of surface seawater, known as '''[[Ocean acidification]]'''. The reduction amounts to 0.1 units; this is an equivalent to a 30% increase in the concentration of hydrogen ions. If the CO<sub>2</sub> emissions from human activities rise on current trends then the average pH of the oceans could fall by 0.5 units by the year 2100.
  
This fall in pH may have a huge impact on marine organisms, in particular  to calcifying organisms such as most mollusks, corals, echinoderms, foraminifera and calcareous algae. Seawater has to be supersaturated with [[calcium]] and [[carbonate ions]] to ensure that once the biogenic calcareous structures are formed, it does not dissolve. Lower pH reduces the carbonate saturation of the seawater, making calcification harder.
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This fall in pH may have a huge impact on marine organisms, in particular  to calcifying organisms such as most mollusks, corals, echinoderms, foraminifera and calcareous algae. Seawater has to be supersaturated with calcium and carbonate ions to ensure that once the biogenic calcareous structures are formed, it does not dissolve. Lower pH reduces the carbonate saturation of the seawater, making calcification harder.  
  
 
There is also a difference in vulnerability between the groups of organisms: corals and a group of mollusks ([[Pteropods|pteropods]]) precipitate aragonite; [[Coccolithophorids|coccolithophores]] and [[Foraminifera|foraminifers]] produce the less soluble calcite. Furthermore differs the function (e.g. metabolic or structural function) from the carbonate between the different groups and this is coupled to the sensitivity for acidification. It is likely as CO<sub>2</sub> levels increases, changes of species composition will occur because of the different responses of the species. An altered species composition may have a huge effect on the global carbon cycle.<ref name="Orr"> Orr, J.C.; Fabry, V.J.; Aumont, O.; Bopp, L.; Doney, S.C.; Feely, R.A.; Gnanadesikan, A.; Gruber, N.; Ishida, A.; Joos, F.; Key, R.M.; Lindsay, K.; Maier-Reimer, E.; Matear, R.J.; Monfray, P.; Mouchet, A.; Najjar, R.; Plattner, G.-K.; Rodgers, K.B.; Sabine, C.L.; Sarmiento, J.L.; Schlitzer, R.; Slater, R.D.; Totterdell, I.J.; Weirig, M.-F.; Yamanaka, Y.; Yool, A. (2005). Anthropogenic ocean acidification over the twenty-first century and its impact on calcifying organisms.'' Nature (Lond.) 437(7059) '': 681-686.</ref>
 
There is also a difference in vulnerability between the groups of organisms: corals and a group of mollusks ([[Pteropods|pteropods]]) precipitate aragonite; [[Coccolithophorids|coccolithophores]] and [[Foraminifera|foraminifers]] produce the less soluble calcite. Furthermore differs the function (e.g. metabolic or structural function) from the carbonate between the different groups and this is coupled to the sensitivity for acidification. It is likely as CO<sub>2</sub> levels increases, changes of species composition will occur because of the different responses of the species. An altered species composition may have a huge effect on the global carbon cycle.<ref name="Orr"> Orr, J.C.; Fabry, V.J.; Aumont, O.; Bopp, L.; Doney, S.C.; Feely, R.A.; Gnanadesikan, A.; Gruber, N.; Ishida, A.; Joos, F.; Key, R.M.; Lindsay, K.; Maier-Reimer, E.; Matear, R.J.; Monfray, P.; Mouchet, A.; Najjar, R.; Plattner, G.-K.; Rodgers, K.B.; Sabine, C.L.; Sarmiento, J.L.; Schlitzer, R.; Slater, R.D.; Totterdell, I.J.; Weirig, M.-F.; Yamanaka, Y.; Yool, A. (2005). Anthropogenic ocean acidification over the twenty-first century and its impact on calcifying organisms.'' Nature (Lond.) 437(7059) '': 681-686.</ref>
  
==Effects on coastal organism== 
 
 
The main threat for coastal organisms is loss of habitat, due to the higher sea level and an increase of the storm frequency. Increased storminess will result in erosion, retreat of beaches, and dune scarping with vegetation loss. For example, Europe accommodates a significant number of shorebirds in winter. Shorebird numbers depend on intertidal areas, so [[Sea level rise|sea-level rise]] could reduce the carrying capacity for these shorebirds.<ref name="Nicholls"> Nicholls, R.J.; Klein, R.J.T. (2005). Climate change and coastal management in Europe's coast, '''in''': Vermaat, J.E. ''et al.'' (Ed.) (2005). Manging European coasts: past, present and future. pp. 199-226. </ref>
 
 
Average sea level rise is predicted to be up to 90 cm by the year 2100. The highly adaptable sandy-shore biota will not be at direct risk from it. Onshore migration is the natural ecosystem response to rising sea levels, but this is stopped by fixed sea defenses. Beaches are trapped in a ‘coastal squeeze’ (Fig.3) between the impacts of urbanization on the terrestrial side and manifestations of climate change at sea. While unconstrained, beaches are resilient, changing shape and extent naturally in response to storms and variations in wave climate and currents. However, human modifications of the coastal zone severely limit this flexibility.<ref name="Nordstrom"> Nordstrom, K.F. (2000). Beaches and dunes on developed coasts. Cambrige University Press, Cambridge, UK, '''in''': Schlacher, T.A.; Dugan, J.; Schoeman, D.S.; Lastra, M.; Jones, A.; Scapini, F.; McLachlan, A.; Defeo, O. (2007). Sandy beaches at the brink. ''Diversity and Distribution''.</ref>This implements a fundamental conflict between protecting socio-economic activity and sustaining the ecological functioning of the coastal zone in Europe under rising sea levels. It suggests a need for more soft protection (nourishment), managed retreat, and possibly accommodation strategies. <ref name="Nicholls"> Nicholls, R.J.; Klein, R.J.T. (2005). Climate change and coastal management in Europe's coast, '''in''': Vermaat, J.E. ''et al.'' (Ed.) (2005). Manging European coasts: past, present and future. pp. 199-226. </ref> <ref name="McLachlan"> McLachlan, A.; Brown, A.C. (2006). The ecology of sandy shores. 2nd. Edition. Academic Press: Amsterdam, The Netherlands. 373 pp. </ref>
 
 
Even ‘soft’ engineering solutions are not free of negative ecological consequences. The ecological consequences of engineering activities on beaches include the loss of biodiversity, productivity, and critical habitats as well as modifications of the subtidal zone which is an important recruitment zone for many sandy beach animals.<ref name="Dugan"> Dugan, J.E. & Hubbard, D.M. (2006). Ecological responses to coastal armouring on exposed sandy beaches. ''Shore and Beach'' 74: 10-16. '''in''': Schlacher, T.A.; Dugan, J.; Schoeman, D.S.; Lastra, M.; Jones, A.; Scapini, F.; McLachlan, A.; Defeo, O. (2007). Sandy beaches at the brink. ''Diversity and Distribution''.</ref> <ref name="Peterson1"> Peterson, C.H. & Bishop, M.J. (2005). Assessing the environmental impacts of beach nourishment. ''Bioscience'' 55: 887-896. '''in''': Schlacher, T.A.; Dugan, J.; Schoeman, D.S.; Lastra, M.; Jones, A.; Scapini, F.; McLachlan, A.; Defeo, O. (2007). Sandy beaches at the brink. ''Diversity and Distribution''.</ref> <ref name="Peterson2"> Peterson, C.H.; Bishop, M.J., Johnson, G.A.; D’Anna, L.M. & Manning, L.M. (2006). Exploiting beach filling as an unaffordable experiment: benthic intertidal impacts propagating upwards to shorebirds. ''Journal of Experimental Marine Biology and Ecology'' 338: 205-221. '''in''': Schlacher, T.A.; Dugan, J.; Schoeman, D.S.; Lastra, M.; Jones, A.; Scapini, F.; McLachlan, A.; Defeo, O. (2007). Sandy beaches at the brink. ''Diversity and Distribution''.</ref> <ref name="Speybroeck"> Speybroeck, J.; Bonte, D.; Courtens, W.; Gheskiere, T.; Grootaert, P.; Maelfait, J.P.; Mathys, M.; Provoost, S.; Sabbe, K.; Stienen, E.W.M.; Van Lancker, V.; Vincx, M. & Degraer, S. (2006). Beach nourishment: an ecologically sound coastal defence alternative? A revieuw. Aquatic conservation – Marine and Freshwater Ecosystems 16: 419-435. '''in''': Schlacher, T.A.; Dugan, J.; Schoeman, D.S.; Lastra, M.; Jones, A.; Scapini, F.; McLachlan, A.; Defeo, O. (2007). Sandy beaches at the brink. ''Diversity and Distribution''.</ref>
 
 
[[Image:coastalsqueeze.jpg|centre|300px| Fig.3: Coastal squeeze    SOURCE: www3.hants.gov.uk|frame]]
 
  
 
==Effects at the level of physiological responses to temperature rise==
 
==Effects at the level of physiological responses to temperature rise==
  
 
Temperature rise for the oceans as a whole is likely to be about 1 to 2 °C, in the next decades. Exceptions are semi enclosed marine lagoons and shallow bays that may mirror the atmospheric temperature rise as well. Additional, most aquatic sandy-shore animals are adapted to rapid changes in temperature and they seldom experience temperatures close to their upper tolerance limits. Further, sandy-beach animals are capable of burrowing  and of escaping below the sand if conditions at the surface become hostile. <ref name="McLachlan"> McLachlan, A.; Brown, A.C. (2006). The ecology of sandy shores. 2nd. Edition. Academic Press: Amsterdam, The Netherlands. 373 pp.</ref>
 
Temperature rise for the oceans as a whole is likely to be about 1 to 2 °C, in the next decades. Exceptions are semi enclosed marine lagoons and shallow bays that may mirror the atmospheric temperature rise as well. Additional, most aquatic sandy-shore animals are adapted to rapid changes in temperature and they seldom experience temperatures close to their upper tolerance limits. Further, sandy-beach animals are capable of burrowing  and of escaping below the sand if conditions at the surface become hostile. <ref name="McLachlan"> McLachlan, A.; Brown, A.C. (2006). The ecology of sandy shores. 2nd. Edition. Academic Press: Amsterdam, The Netherlands. 373 pp.</ref>
This is in contrast to sessile organisms such as corals and mangroves that are unable to keep up with the higher temperature level.  
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This is in contrast to sessile organisms such as corals and mangroves that are unable to keep up with the higher temperature level.
  
==Effects on [[Estuary|estuaries]]==
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== See also ==
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*[[Natural variability and change in coastal ecosystems]]
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*[[Effects of climate change on the Mediterranean]]
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*[[Effects of climate change on the North Atlantic benthos]]
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*[[Effects of climate change on the North Sea and Baltic Sea]]
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*[[Climate change leads to Arctic food shortages]]
  
Sea level rise will result in saltwater intrusion that wreaks havoc with freshwater ecosystems, including rivers, freshwater marshes and coastal lowland farm acreage.
 
Changes in strength and seasonality can affect the retention-dispersion mechanism of planktonic larvae (Gaines and Bertness 1992 in 1). A change in precipitation will affect estuaries through enhanced river runoff and changes in nutrients and salinity. Al these physical disturbances  affect the ecosystem functions and the species assemblages.
 
  
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==References==
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<references/>
  
  
 
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[[Category:Climate change, impacts and adaptation]]
 
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[[Category:Coastal and marine ecosystems]]
 
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[[Category:Marine Biodiversity‏‎]]
==References==
 
 
 
<references/>
 
  
 
{{author
 
{{author
|AuthorName=Therry, Lieven}}
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|AuthorID=15336
[[Category:Theme 7]]
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|AuthorFullName=Therry, Lieven
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|AuthorName=Ltherry}}

Revision as of 11:22, 3 September 2020

This article discusses global warming and the range of effects on marine systems. The effects may be related to changing water temperatures, changing water circulation or changing habitat; as a consequence of these changes, altered pathways within biogeochemical cycles and food webs are detected as well. In the first case, the biological responses and impacts result from the physical effects.[1]

Even without human-induced climate change, the biodiversity and biogeography of species is continuously changing (seasonal and yearly changes). Consequently, long term monitoring is necessary in order to evaluate these processes. The marine systems however may become more dynamic and variable due to climate change.[1]

Coastal ecosystems of the enclosed seas such as the Baltic, the Mediterranean and the Black Sea are most threatened bu climate change. These seas have only small and primarily east-west orientated movement corridors, which may restrict northward displacement of organisms in these areas.[2]


Effects on primary production

Higher temperatures and enhanced stratification could affect the productivity of phytoplankton. A number of models predict an increase in global primary production of between 1% and 8% by 2050, when compared to pre-industrial times.[3]

Because phytoplankton is an important basis of the marine food web, any change in the timing, abundance or species composition of the phytoplankton will have an effect on the whole food web.[1]

Effects on the recruitment process

The population dynamics of a lot of marine vertebrates and fish are driven by recruitment processes. The recruitment of cold temperate species is often synchronized with seasonal production cycles of phytoplankton. Increasing sea water temperatures may advance the timing of reproduction of these fish species; this may result in a mismatch with their food source (phytoplankton) (match/mismatch hypothesis). A change in recruitment success will lead to shifts in species composition.[1]

Example: cod recruitment in the North Sea

The Atlantic cod (Gadus morhua) recruitment in the North Sea, in the past 40 years, was influenced by changes at the base of the food web (bottom-up-control), induced by the rise of temperature. Cod recruitment decreased from the mid-1980s, coincident with unfavorable changes in the plankton ecosystem.[4]

Atlantic cod Gadus morhua SOURCE: www.fishbase.org
Long-term changes (1958-1999) in the plankton index (in black), and long-term changes (1959-2000) in cod recruitment (in red, decimal logarithm).(Biological parameters for the diet and growth of cod larvae and juveniles: total calanoid copepods (qualitative indicator of food for larval cod), the mean size of calanoid copepods (qualitative indicator of food) and the abundance of two dominant congeneric species (Calanus finmarchicus and C. helgolandicus). Reprinted by permission from Macmillan Publishers Ltd: [NATURE] (Beaugrand, G.; Brander, K.M.; Lindley, J.A.; Souissi, S.; Reid, P.C. (2003). Plankton effect on cod recruitment in the North Sea. Nature (Lond.) 426(6967): 661-664.), copyright (2003)

Effects on the biogeography

The species movement in a warming area is towards the poles in general. Since global warming accelerated in the late 1980s, pole ward advances of southern species and retreats of northern species have been recorded in zooplankton, fish and benthic species.[5] .[6]

The species distribution is not always northwards. For example when the stock of the main prey of the harp seals in the Barents Sea collapsed, these seals migrated southwards along the coast of Norway and into the North Sea in search of food.[1]

Example: Study of barnacles in the Celtic-Biscay shelf

Long-term changes in Semibalanus balanoides and Chthamalus spp. for several shores at different submersion levels (HWN: High Water Neap; MTL: Mean Tidal Low; LWN: Low Water Neap) on the south coast of Devon and Cornwall. SOURCE: © Southward 1995[7]

The Celtic-Biscay shelf was liable to warming in the 1930; in the 1960 there was a switch back to colder. Changes in species assemblages were described on rocky shores, using barnacles as a sensitive indicator of wider changes in marine life.[7] [6] These showed switches between warm water barnacles in the 1950s (Chthamalus spp.) to greater dominance by the cold water barnacle Semibalanus balanoides in the 1960s and 1970s. On rocky shores warm water barnacles now exceed the levels found in the 1950s.[1]


There are also examples from the North Sea and the Baltic Sea.






Effects on the phenological relationships and community structure

The response to climate changes differs between the species, inducing a decoupling of phenological relationships (relative timing of life cycle events). The decoupling may affect the community structure and food webs by altering the interactions between a species and its competitors, mutualists, predators, prey or pathogens. For example, in the case of seabirds, chick diet composition during development is likely to be an important mechanistic link between climate variability and the observed decline in seabird populations.[8]

A study in Kongsfjorden (79 °N) concluded that changing temperatures have a direct and very immediate influence on the species composition of plankton as well as on the biodiversity. The response of benthic organisms to rising temperature is slower and less drastic compared with planktonic organisms. Planktonic organisms may be a better indicator of global warming-driven changes than the benthic organisms. However benthic fauna is a good indicator of slow changes, especially when observed over a long period of time.[9]

Effects on the establishment of invasive species

Pacific oyster Crassostrea gigas SOURCE: www.spirula.nl

The establishment of non-indigenous species can be accelerated by rapid warming. For example, the recent warming has accelerated the adaptation of the Pacific oyster (Crassostrea gigas) on the local circumstances in the Netherlands and the UK.[10]


Effects on biogeochemical cycles

In the past 200 years the oceans have absorbed approximately half of the CO2 produced by fossil fuel burning and cement production. Calculations indicate that this uptake of CO2 has led to a reduction of the pH of surface seawater, known as Ocean acidification. The reduction amounts to 0.1 units; this is an equivalent to a 30% increase in the concentration of hydrogen ions. If the CO2 emissions from human activities rise on current trends then the average pH of the oceans could fall by 0.5 units by the year 2100.

This fall in pH may have a huge impact on marine organisms, in particular to calcifying organisms such as most mollusks, corals, echinoderms, foraminifera and calcareous algae. Seawater has to be supersaturated with calcium and carbonate ions to ensure that once the biogenic calcareous structures are formed, it does not dissolve. Lower pH reduces the carbonate saturation of the seawater, making calcification harder.

There is also a difference in vulnerability between the groups of organisms: corals and a group of mollusks (pteropods) precipitate aragonite; coccolithophores and foraminifers produce the less soluble calcite. Furthermore differs the function (e.g. metabolic or structural function) from the carbonate between the different groups and this is coupled to the sensitivity for acidification. It is likely as CO2 levels increases, changes of species composition will occur because of the different responses of the species. An altered species composition may have a huge effect on the global carbon cycle.[11]


Effects at the level of physiological responses to temperature rise

Temperature rise for the oceans as a whole is likely to be about 1 to 2 °C, in the next decades. Exceptions are semi enclosed marine lagoons and shallow bays that may mirror the atmospheric temperature rise as well. Additional, most aquatic sandy-shore animals are adapted to rapid changes in temperature and they seldom experience temperatures close to their upper tolerance limits. Further, sandy-beach animals are capable of burrowing and of escaping below the sand if conditions at the surface become hostile. [12] This is in contrast to sessile organisms such as corals and mangroves that are unable to keep up with the higher temperature level.

See also


References

  1. 1.0 1.1 1.2 1.3 1.4 1.5 Phillipart C.J.M. (ed.) (2007). Impacts of climate change on the European marine and coastal environment: ecosystems approach. European Science Foundation, Marine Board: Strasbourg, France. 82pp.
  2. Nicholls, R.J.; Klein,R.J.T. (2005). Climate change and coastal management on Europe's coast, in: Vermaat, J.E. et al. (Ed.) (2005). Managing European coasts: past, present and future. pp. 199-226.
  3. Sarmiento, J.L.; Slater, R.; Barber, R.; Bopp, L.; Doney, S.C.; Hirst, A.C., Kleypas, J.; Matear, R.; Mikolajewicz, U.; Monfray, P.; Soldatov, V.; Spall, S.A.; Stouffer, R. (2004). Response of ocean ecosystems to climate warming. Glob Biogeoch Cycles 18,3. cit. in: Philippart, C.J.M. (Ed.). (2007). Impacts of climate change on the European marine and coastal environment: ecosystems approach. ESF Marine Board Position Paper. European Science Foundation, Marine Board: Strasbourg, France. 82 pp.
  4. Beaugrand, G.; Brander, K.M.; Lindley, J.A.; Souissi, S.; Reid, P.C. (2003). Plankton effect on cod recruitment in the North Sea.Nature (Lond.) 426(6967): 661-664.
  5. Brander, K.; Blom, G.; Borges, M.F.; Erzini, K.; Henderson, G.; MacKenszie, B.R.; Mendes, H.; Ribeiro, J.; Santos, A.M.P.; Toresen, T. (2003). Changes in fish distribution in the eastern North Atlantic: Are we seeing a coherent response to changing temperature? ICES Mar Sci Symp 219: 261-270. cit. in: Philippart, C.J.M. (Ed.). (2007). Impacts of climate change on the European marine and coastal environment: ecosystems approach. ESF Marine Board Position Paper. European Science Foundation, Marine Board: Strasbourg, France. 82 pp.
  6. 6.0 6.1 Southward, A.J.; Langmead, O.; Hardman-Mountford, N.J.; Aiken, J.; Boalch, G.T.; Dando, P.R.; Genner, M.J.; Joint, I.; Kendall, M; Halliday, N.C.; Harris, R.P.; Leaper, R.; Mieszkowska, N.; Pingree, R.D.; Richardson, A.J.; Sims, D.W.; Smith, T.; Walne, A.W.; Hawkins, S.J. (2005). Long term oceanographic and ecological research in the western English Channel. Adv Mar Biol 47: 1-105 cit. in: Philippart, C.J.M. (Ed.). (2007). Impacts of climate change on the European marine and coastal environment: ecosystems approach. ESF Marine Board Position Paper. European Science Foundation, Marine Board: Strasbourg, France. 82 pp. Cite error: Invalid <ref> tag; name "Southward2005" defined multiple times with different content
  7. 7.0 7.1 Southward, A.J.; Hawkins, S.J.; Burrowa, M.T. (1995). Seventy years` observations of changes in distribution and abundance of zooplankton and intertidal organisms in the western English Channel in relation to rising sea temperature. J Therm Biol 20: 127-155. cit. in: Philippart, C.J.M. (Ed.). (2007). Impacts of climate change on the European marine and coastal environment: ecosystems approach. ESF Marine Board Position Paper. European Science Foundation, Marine Board: Strasbourg, France. 82 pp. Cite error: Invalid <ref> tag; name "Southward1995" defined multiple times with different content
  8. Kitaysky, A.S.; Kitaiskaia, E.V.; Piatt, J.F.; Wingfield, J.C. (2005). A mechanistic link between chick diet and decline in seabirds? Proc Biol Sci Proc R Soc B 273:445-450. cit. in: Phillipart C.J.M. (ed.) (2007). Impacts of climate change on the European marine and coastal environment: ecosystems approach.ESF Marine Board Position Paper. European Science Foundation, Marine Board: Strasbourg, France. 82 pp.
  9. Kedra, M.; Walkusz, W. (2006). Global warming-driven biodiversity change: pelagic versus benthic domain [Arctic 79°N case study] MarBEF Newsletter 5: 23-24.
  10. Essink, K.; Dettmann, C.; Farke, H.; Laursen, K.; LuerBen, G.; Marencic, H.; Wiersinga, W. (Eds). Wadden Sea Quality Status Report 2004. Wadden Sea Ecosystems 19-2005, 155-161pp. cit. in: Phillipart C.J.M. (ed.) (2007). Impacts of climate change on the European marine and coastal environment: ecosystems approach.ESF Marine Board Position Paper. European Science Foundation, Marine Board: Strasbourg, France. 82 pp.
  11. Orr, J.C.; Fabry, V.J.; Aumont, O.; Bopp, L.; Doney, S.C.; Feely, R.A.; Gnanadesikan, A.; Gruber, N.; Ishida, A.; Joos, F.; Key, R.M.; Lindsay, K.; Maier-Reimer, E.; Matear, R.J.; Monfray, P.; Mouchet, A.; Najjar, R.; Plattner, G.-K.; Rodgers, K.B.; Sabine, C.L.; Sarmiento, J.L.; Schlitzer, R.; Slater, R.D.; Totterdell, I.J.; Weirig, M.-F.; Yamanaka, Y.; Yool, A. (2005). Anthropogenic ocean acidification over the twenty-first century and its impact on calcifying organisms. Nature (Lond.) 437(7059) : 681-686.
  12. McLachlan, A.; Brown, A.C. (2006). The ecology of sandy shores. 2nd. Edition. Academic Press: Amsterdam, The Netherlands. 373 pp.
The main author of this article is Therry, Lieven
Please note that others may also have edited the contents of this article.

Citation: Therry, Lieven (2020): Effects of global climate change on European marine biodiversity. Available from http://www.coastalwiki.org/wiki/Effects_of_global_climate_change_on_European_marine_biodiversity [accessed on 28-03-2024]