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WGE 29th session, September 2010 1Brit Lisa Skjelkvåle ITEM 4 Acidification and eutrophication ICP Waters ECE/EB.AIR/WG.1/2010/6
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WGE 29th session, September 2010 2Brit Lisa Skjelkvåle Effects of atmospheric N deposition on biology in oligotrophic surface waters ICP Waters report 101/2010 Has atmospheric N deposition contributed to nutrient enrichment of lakes and rivers?
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WGE 29th session, September 2010 3Brit Lisa Skjelkvåle Background-1: is algal growth limited by phosphorus, nitrogen, CO 2 ? Debate on causes of eutrophication in 1970s Schindler’s ‘whole lake fertilization experiments’ in Experimental Lake Area in Canada Conclusion: P controls primary productivity
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WGE 29th session, September 2010 4Brit Lisa Skjelkvåle Background-2 P-limitation of algal growth in freshwaters is textbook knowledge Effects of N deposition studied in relation to acidification Recent studies indicate that N supply affects algal growth ICP Waters report: – to give overview of literature on effects of reactive N in freshwaters – to improve/extend critical loads for nutrient nitrogen for freshwaters
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WGE 29th session, September 2010 5Brit Lisa Skjelkvåle Effects of atmospheric N deposition on N leaching N deposition leads to increased leaching of nitrate to surface waters in natural ecosystems Leaching of N highly dependent on catchment type Kaste ea 2008
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WGE 29th session, September 2010 6Brit Lisa Skjelkvåle Effects of N in freshwaters Experimental evidence – Whole-lake experiments – Smaller scale in-situ experiments – Laboratory studies Historical records: – Lake sediment studies (paleolimnology) Monitoring studies – Region-wide lake surveys
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WGE 29th session, September 2010 7Brit Lisa Skjelkvåle Lake ecosystem Free-floating algae Benthic algae Lake sediments Water plants
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WGE 29th session, September 2010 8Brit Lisa Skjelkvåle Experimental evidence ’Whole-lake’ experiments – Expensive, but high ecological realism – Additions with P and N show changes in algal growth and algal species – N can be a limiting factor Mesocosm experiments – Less expensive and less realistic – Pelagic (”free-floating”) algae can respond to N addition only – Benthic (”rock-dwelling”) algae can also respond but less clearly
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WGE 29th session, September 2010 9Brit Lisa Skjelkvåle Experimental evidence Nitrogen is (co)limiting factor for growth of phytoplankton and benthic algae No direct link between response to N and N deposition Critical loads need a relation between N deposition and a certain biological response
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WGE 29th session, September 2010 10Brit Lisa Skjelkvåle Historical records: paleolimnological evidence Most studies from arctic and alpine lakes N deposition below 5 kg N/ha/yr Types of response: – Sediments enrichment with 15 N which indicates an atmospheric source – Changes in algal community structure (species diversity) – Statistical correlations between species diversity and N enrichment – Climate change is also partly responsible for observed changes
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WGE 29th session, September 2010 11Brit Lisa Skjelkvåle Monitoring: lake surveys Strength: – data from many regions – Possible to relate N deposition to a response Weakness: – other factors than N deposition may control the response Bergstrøm and Jansson 2006
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WGE 29th session, September 2010 12Brit Lisa Skjelkvåle Higher productivity with higher N deposition More NO 3 at higher N deposition Higher algal production where N deposition was high (corrected for P) Clearest effect at N dep < 5 kg N/ha/yr N deposition ---- [NO3] Algal biomass Bergstrøm and Jansson 2006
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WGE 29th session, September 2010 13Brit Lisa Skjelkvåle Nitrogen enrichment effects on water plants (macrophytes) Worldwide loss of typical acid-sensitive communities adapted to low N availability (isoetides) Increased growth of more nitrophilous species Especially well-documented in the Netherlands Related to N-availability and –form Also related to alkalinity and nutrients in sediments Critical load 5-10 kg N/ha/yr (Bobbink ea 1995 WASP)
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WGE 29th session, September 2010 14Brit Lisa Skjelkvåle Conclusions Atmospheric N deposition leads to N-enrichment of oligotrophic lakes in arctic, alpine and boreal regions Evidence from paleolimnology, whole-lake and smaller scale experiments, regional surveys – increased productivity – shifts in algal communities – loss of rare macrophyte species, increase of other (nuisance) species – data scarcity on effects on benthic algae and effects at higher trophic levels
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WGE 29th session, September 2010 15Brit Lisa Skjelkvåle Empirical CLs
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WGE 29th session, September 2010 16Brit Lisa Skjelkvåle Suggestions for further development CLs for nutrient-N for freshwaters Catchment characteristics determine catchment N retention capacity FAB model is presently used to model critical loads for acidity by simulation of NO 3 leaching as a function of catchment characteristics Use FAB model also in modelling of nutrient-N CLs for freshwaters?
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