Climate Change and the European Water Dimension - Agri ...
Climate Change and the European Water Dimension - Agri ...
Climate Change and the European Water Dimension - Agri ...
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<strong>and</strong> possibly elimination of seasonal migrants to shallow, ice-covered winterkill lakes.<br />
In temperate region, on <strong>the</strong> contrary, <strong>the</strong> risk of winter fish-kills is smaller in warmer<br />
winters. In response to higher temperatures, nor<strong>the</strong>rn boreal populations of cyprinid<br />
<strong>and</strong> percid fish species are expected to increase at <strong>the</strong> expense of coldwater,<br />
salmonid species (Lehtonen, 1996). Shallow lakes would be most susceptible to<br />
<strong>the</strong>se changes because of <strong>the</strong>ir lack of <strong>the</strong>rmal stratification. Total freshwater fish<br />
production is expected to increase, but with <strong>the</strong> projected changes in <strong>the</strong> composition<br />
of fish fauna, <strong>the</strong> recreational <strong>and</strong> commercial value of catches will decrease<br />
(Lehtonen, 1996).<br />
IV.B.10. Ecosystem response of lakes<br />
In conclusion, different species as well as physical <strong>and</strong> chemical properties react<br />
differently because of <strong>the</strong>ir different interactions in <strong>the</strong> foodweb. However, some<br />
changes might be relevant on a species level, but all <strong>the</strong>se single effects may weigh<br />
differently in <strong>the</strong> lake ecosystem as a whole. Petchy et al. (1999) conducted<br />
microcosm experiments to control species composition <strong>and</strong> rates of environmental<br />
change. They suggested that ecosystem responses are not as clear as studies of<br />
single trophic levels indicate. Complex responses generated in entire food webs<br />
greatly complicate inferences based on single functional groups. Here, <strong>the</strong><br />
consideration of more general ecological concepts is needed in order to underst<strong>and</strong><br />
<strong>and</strong> syn<strong>the</strong>size climatic effects on lake ecosystems. The strength of food web<br />
interactions is characterized by many weak <strong>and</strong> few strong interactions (McCann et<br />
al., 1998). Weak links in particular act to dampen oscillations between consumers<br />
<strong>and</strong> resources (McCann et al., 1998) <strong>and</strong> presumably also environmental stressors,<br />
as climate extremes. This means that not all responses at a specific trophic level are<br />
propagated to lower trophic levels or have significant impacts on ecosystem<br />
processes (Pace et al., 1999). Additionally, a prolongation due to food web<br />
interactions is possible as <strong>the</strong> signal of winter climate can be detected in <strong>the</strong> clear<br />
water phase in early summer (Straile <strong>and</strong> Adrian, 2000) or in <strong>the</strong> summer<br />
phytoplankton composition <strong>and</strong> biomass (Weyhenmeyer, 2001; Blenckner et al.,<br />
2002). A system approach is necessary to examine <strong>the</strong> cascading effects in<br />
response to climatic change <strong>and</strong> variability. The magnitude of a climate-driven<br />
response of an autotrophic organism is not necessarily mediated or cascaded to <strong>the</strong><br />
heterotrophic species, or vice versa. The potential for misleading inferences has<br />
been highlighted (Harrington et al., 1999). Fur<strong>the</strong>rmore, <strong>the</strong> non-linearity in <strong>the</strong><br />
response to environmental variables (including climate) of animal <strong>and</strong> plants should<br />
be remembered (May, 1986; Mysterud et al., 2001), as smooth changes can be<br />
interrupted by drastic switches to a contrasting state of <strong>the</strong> ecosystem function<br />
(Scheffer et al., 2001).<br />
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