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Climate Change and the European Water Dimension - Agri ...

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have recently described a method that can be used to ‘hindcast’ <strong>the</strong> seasonal<br />

variation in <strong>the</strong> residence time of a lake. Using this system, some lakes are classified<br />

as ‘one season’ lakes which respond very quickly to changes in <strong>the</strong> rainfall whilst<br />

o<strong>the</strong>rs are ‘multi-season’ lakes that are influenced by <strong>the</strong> changes recorded over<br />

months or even years. In UK <strong>the</strong> most pronounced changes will thus be recorded in<br />

<strong>the</strong> ‘wet’ west during <strong>the</strong> winter <strong>and</strong> <strong>the</strong> dry ‘east’ during <strong>the</strong> summer.<br />

Figure IV.B.3 shows <strong>the</strong> effect that historical variations in <strong>the</strong> rainfall have had on <strong>the</strong><br />

winter residence time of Esthwaite <strong>Water</strong>, a lake with an average annual residence<br />

time of 92 days. The results show that <strong>the</strong> winter residence time of this lake has<br />

decreased progressively over <strong>the</strong> past 40 years with <strong>the</strong> rate of decline averaging 0.5<br />

days a year. Lakes with long residence times are less sensitive to <strong>the</strong> effects of<br />

changes in <strong>the</strong> rainfall since <strong>the</strong> effects of heavy winter rains may <strong>the</strong>n counter <strong>the</strong><br />

impact of summer droughts. An increase in <strong>the</strong> water residence time in a warmer<br />

climate due to higher evaporation <strong>and</strong> decreased stream outflow will also increase<br />

<strong>the</strong> retention of chemical constituents, <strong>and</strong> intensify <strong>the</strong> nutrient cycle.<br />

To summarize, in deep perialpine lakes (north <strong>and</strong> south of <strong>the</strong> Alps) climate<br />

changes are having a double <strong>and</strong> contrasting impact on <strong>the</strong> renewal times of lake<br />

waters. In summer, an increase in <strong>the</strong> thickness of <strong>the</strong> mixo-limnion accelerates <strong>the</strong><br />

renewal time, as a greater volume of water is involved. In winter, <strong>the</strong> need for more<br />

mixing energy to trigger a complete vertical mixing, or a deeper mixing, reduces <strong>the</strong><br />

volume of <strong>the</strong> water mass involved in <strong>the</strong> renewal.<br />

<strong>Water</strong> level<br />

Because of <strong>the</strong> intimate hydrological link between river discharge <strong>and</strong> lake level,<br />

changes in run-off will ultimately influence lake level characteristics. Increasing<br />

trends in heavy rainfalls (Osborne <strong>and</strong> Hulme, 2002; Matulla et al., 2004) will affect<br />

lake levels <strong>and</strong> increase <strong>the</strong> flood risk.<br />

<strong>Climate</strong> change has introduced ano<strong>the</strong>r level of uncertainty to <strong>the</strong> management of<br />

most dams. The safety of large dams is affected by changes in <strong>the</strong> magnitude or<br />

frequency of extreme precipitation events. One of <strong>the</strong> first studied in this area<br />

concluded that <strong>the</strong> discharge of <strong>the</strong> 50-year flood on <strong>the</strong> River Severn in <strong>the</strong> United<br />

Kingdom might increase by approximately 20% by 2050 (Tedd, 2000). There is<br />

concern whe<strong>the</strong>r existing spillways of large dams can accommodate such floods in<br />

<strong>the</strong> future.<br />

In <strong>the</strong> flat l<strong>and</strong>scapes in Estonia, N-W Russia, South Finl<strong>and</strong> <strong>and</strong> North Germany<br />

where <strong>the</strong> outflow from lakes is often limited by <strong>the</strong> small slope of rivers, changes in<br />

precipitation result in large seasonal <strong>and</strong> interannual fluctuations of <strong>the</strong> water level.<br />

<strong>Change</strong>s in water levels, particularly in shallow lakes, may change <strong>the</strong> mean water<br />

column irradiance (Behrendt <strong>and</strong> Stellmacher, 1987) <strong>and</strong> shift areas of sediment<br />

erosion, transportation, <strong>and</strong> accumulation (Bengtsson et al. 1990). The large surface<br />

area to mean depth ratio makes <strong>the</strong> shallow lakes, especially large ones, highly<br />

susceptible to climatic influences (Magnusson et al. 1990). The responses of phyto-<br />

<strong>and</strong> zooplankton communities to altered environmental conditions may be complex<br />

(Weyhenmeyer et al. 1999; Nõges <strong>and</strong> Nõges, 1999; Irigoien et al. 2000; Gerten <strong>and</strong><br />

Adrian 2000; Straile 2000; Straile <strong>and</strong> Adrian 2000). Generally, shorter residence<br />

time <strong>and</strong> higher water levels in lakes will contribute to <strong>the</strong> improvement of all<br />

common water quality parameters in <strong>the</strong>se temperate lakes.<br />

Lake levels in semi-arid <strong>and</strong> arid areas reflect a sensitive balance between water<br />

inflow <strong>and</strong> evaporation. Increasing temperature <strong>and</strong> prolonged droughts decrease <strong>the</strong><br />

water level in <strong>the</strong>se lakes <strong>and</strong> shift <strong>the</strong>m from a permanent status to a semi-<br />

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