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

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Most of <strong>the</strong> processes in nutrient cycles are biologically mediated <strong>and</strong> thus<br />

temperature-dependent.<br />

Nitrate concentration (de-trended)<br />

800<br />

400<br />

0<br />

-400<br />

-800<br />

1960 1970 1980 1990 2000<br />

Year<br />

Figure IV.B.4. De-trended winter nitrate data for Blelham Tarn<br />

Catchment processes<br />

Melting of glaciers <strong>and</strong> loss of soil permafrost in catchments of high alpine <strong>and</strong> sub<br />

arctic lakes as a result of climate warming causes dramatic changes in chemistry <strong>and</strong><br />

biota of <strong>the</strong>se lakes. For example, a temperature increase by two degrees that<br />

melted <strong>the</strong> permafrost <strong>and</strong> left Lake Schwarzensee, a remote high alpine lake in<br />

Austria, ice-free for two months in summer, changed totally <strong>the</strong> regime of <strong>the</strong> lake.<br />

Conductivity <strong>and</strong> silica doubled, <strong>the</strong> lake became warmer <strong>and</strong> hence more<br />

productive, <strong>and</strong> pH dramatically increased (Psenner <strong>and</strong> Schmidt, 1992).<br />

One of <strong>the</strong> simplest measures of this catchment effect is <strong>the</strong> concentration of<br />

nutrients measured in <strong>the</strong> lakes during <strong>the</strong> winter when <strong>the</strong> biological uptake rate is<br />

very low (Sutcliffe et al, 1982). Year-to-year variation in winter air temperature has<br />

been found to influence <strong>the</strong> nitrate concentration in lakes in <strong>the</strong> English Lake District,<br />

as warm winters lead to a reduced nitrate concentration in <strong>the</strong> water (George et al.,<br />

2004). (Figure IV.B.4) shows <strong>the</strong> result of de-trending <strong>the</strong> winter nitrate data for<br />

Blelham Tarn, a small lake in <strong>the</strong> Windermere catchment. Once <strong>the</strong> long-term<br />

‘anthropogenic’ trend has been removed, <strong>the</strong> residual variation is clearly related to<br />

<strong>the</strong> short-term variations in <strong>the</strong> air temperature.<br />

Very similar interannual variations in <strong>the</strong> winter concentration of dissolved reactive<br />

phosphorus have also been detected in de-trended time-series from <strong>the</strong> English<br />

lakes. The most pronounced effects are detected in lakes with relatively short<br />

residence times. The most likely explanation for this trend is <strong>the</strong> effect that heavy rain<br />

has on <strong>the</strong> routing of drainage in <strong>the</strong> catchment. The first step in <strong>the</strong> transfer of<br />

dissolved reactive P (DRP) in <strong>the</strong> drainage system is <strong>the</strong> dissolution of phosphorus<br />

from <strong>the</strong> superficial layers of <strong>the</strong> soil. If <strong>the</strong> rainfall is light, much of <strong>the</strong> dissolved<br />

phosphorus is adsorbed as <strong>the</strong> water passes through <strong>the</strong> soil (Sharpley <strong>and</strong> Sayers,<br />

70<br />

-4<br />

-2<br />

0<br />

2<br />

4<br />

Air temperature ( o C)

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