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Fourth Study Conference on BALTEX Scala Cinema Gudhjem

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- 174 -<br />

Expected Changes in Water Resources Availability and Water Quality with<br />

Respect to Climate Change in the Elbe River Basin<br />

Valentina Krysanova and Fred Hattermann<br />

Potsdam Institute for Climate Impact Research, P.O. Box 601203, Telegrafenberg, 14412 Potsdam<br />

krysanova@pik-potsdam.de<br />

1. Introducti<strong>on</strong><br />

Reliable modelling of climate-water interacti<strong>on</strong>s at the river<br />

basin and regi<strong>on</strong>al scale requires development of advanced<br />

modelling approaches at scales relevant for assessing the<br />

potential effects of climate change <strong>on</strong> hydrological cycle.<br />

These approaches should represent the atmospheric, surface<br />

and subsurface hydrological processes, and take into account<br />

their characteristic temporal and spatial scales of occurrence.<br />

The paper presents a climate change impact assessment for<br />

the Elbe River basin in Germany. The method used for the<br />

study combines<br />

(a) a statistical downscaling method driven by GCMpredicted<br />

temperature trend for producing climate<br />

scenarios, and<br />

(b) an ecohydrological spatially semi-distributed river basin<br />

model.<br />

In additi<strong>on</strong>, a c<strong>on</strong>diti<strong>on</strong>ed M<strong>on</strong>te Carlo simulati<strong>on</strong> was<br />

implemented in the downscaling procedure, so that 100<br />

realizati<strong>on</strong>s of the climate scenario were produced to<br />

investigate the uncertainty of the model predicti<strong>on</strong>s.<br />

2. Case study basin<br />

The study area is the German part of the Elbe River basin<br />

(about 100.000 km 2 ). The l<strong>on</strong>g-term mean annual<br />

precipitati<strong>on</strong> in the basin is 659 mm. The l<strong>on</strong>g-term mean<br />

discharge of the Elbe River is 716 m 3 s -1 at the mouth, and<br />

the specific discharge is 6.2 l s -1 km -2 , which corresp<strong>on</strong>ds to<br />

the mean annual runoff of 10.06 x 10 9 m 3 , or 29.7 % of the<br />

annual precipitati<strong>on</strong>.<br />

A primary reas<strong>on</strong> for selecting this river basin as the case<br />

study regi<strong>on</strong> is its vulnerability against water stress in dry<br />

periods. Due to the positi<strong>on</strong> of the basin around the<br />

boundary between, <strong>on</strong> the <strong>on</strong>e hand, the relatively wet<br />

maritime climate in western Europe and, <strong>on</strong> the other hand,<br />

the more c<strong>on</strong>tinental climate in eastern Europe with l<strong>on</strong>ger<br />

dry periods, the annual l<strong>on</strong>g-term average precipitati<strong>on</strong> is<br />

relatively small. Therefore the Elbe river basin is classified<br />

as the driest am<strong>on</strong>g the five largest river basins in Germany<br />

(Rhine, Danube, Elbe, Weser and Ems) with all resulting<br />

problems and c<strong>on</strong>flicts.<br />

The regi<strong>on</strong> is representative of semi-humid landscapes in<br />

Europe, where water availability during the summer seas<strong>on</strong><br />

is the limiting factor for plant growth and crop yield. The<br />

drainage basin is densely populated, and includes two large<br />

metropolitan areas: Berlin and Hamburg. Within Europe the<br />

Elbe River basin has the sec<strong>on</strong>d lowest water availability per<br />

capita. Due to possible change in circulati<strong>on</strong> patterns and<br />

local orographical c<strong>on</strong>diti<strong>on</strong>s the amount of precipitati<strong>on</strong><br />

will most likely decrease in the Elbe regi<strong>on</strong> (Werner &<br />

Gerstengarbe, 1997).<br />

3. Climate scenario<br />

Currently the resoluti<strong>on</strong> of General Circulati<strong>on</strong> Models<br />

(GCMs) is too rough for correct representati<strong>on</strong> of<br />

hydrological cycle variati<strong>on</strong>s within river basins. The 10 km<br />

climate model resoluti<strong>on</strong>, which is not yet achieved, is a<br />

critical threshold, since at this scale the climate model<br />

outputs become comparable with the scale of hydrological<br />

cycle variati<strong>on</strong>s within catchments, and climate variables<br />

could be predicted without the need for downscaling.<br />

The problem can be partly solved by applying<br />

downscaling methods to transform the GCM outputs <strong>on</strong>to<br />

the regi<strong>on</strong>al or river basin scale. Two main types of<br />

downscaling methods are in use: the deterministic<br />

dynamical downscaling method and the statistical<br />

downscaling method. The deterministic downscaling<br />

models are applied by nesting their grid structure into the<br />

grid structure of GCMs, whereas the outputs of GCMs are<br />

taken as boundary c<strong>on</strong>diti<strong>on</strong>s to calculate climate input<br />

data for regi<strong>on</strong>al applicati<strong>on</strong>s. This type of models is still<br />

under development.<br />

The statistical downscaling method makes use of the<br />

correlati<strong>on</strong> between the large-scale climate patterns (where<br />

the results of GCMs are relatively reliable) and their<br />

regi<strong>on</strong>al representati<strong>on</strong>, c<strong>on</strong>sidering c<strong>on</strong>sistency in<br />

frequency distributi<strong>on</strong>, annual and interannual variability<br />

and persistency of the main climate characteristics. The<br />

advantage of this method is that its results are relatively<br />

robust as l<strong>on</strong>g as the basic climate correlati<strong>on</strong>s in the<br />

observed and scenario periods do not differ. The method<br />

takes the results of GCMs as boundary and initial<br />

c<strong>on</strong>diti<strong>on</strong>s, and therefore the inherent GCM uncertainty is<br />

transferred to the regi<strong>on</strong>al scale as well.<br />

The applied climate scenario was produced by the<br />

statistical downscaling method from the ECHAM4-<br />

OPYC3 GCM, which was driven by the IPCC emissi<strong>on</strong><br />

scenario A1 (F.-W. Gerstengarbe and P. Werner). The<br />

climate change scenario is characterized by an increase in<br />

temperature by 1.4°C until 2050, and a moderate decrease<br />

in mean annual precipitati<strong>on</strong> in the basin corresp<strong>on</strong>ding to<br />

the observed regi<strong>on</strong>al climate trend with notable<br />

subregi<strong>on</strong>al differences. A c<strong>on</strong>diti<strong>on</strong>ed M<strong>on</strong>te Carlo<br />

simulati<strong>on</strong> was implemented in the downscaling<br />

procedure, so that 100 realizati<strong>on</strong>s of the scenario were<br />

produced to investigate the uncertainty of the method.<br />

4. Ecohydrological river basin model and<br />

simulati<strong>on</strong> experiments<br />

The c<strong>on</strong>tinuous-time spatially semi-distributed processbased<br />

ecohydrological model SWIM (Soil and Water<br />

Integrated Model, Krysanova et al., 1998 & 2000)<br />

integrating hydrology, nutrient cycling and vegetati<strong>on</strong><br />

growth at the river basin scale, was used in the study.<br />

The modelling system includes an interface to the<br />

Geographic Informati<strong>on</strong> System GRASS (Geographic<br />

Resources Analysis Support System) (GRASS4.1, 1993).<br />

The spatial disaggregati<strong>on</strong> scheme has three levels: basin –<br />

subbasins – hydrotopes. The subbasin map can be<br />

produced by using the r.watershed operati<strong>on</strong> in GRASS or<br />

input from other sources, and the hydrotope map is usually<br />

produced by overlaying the subbasin, land use and soil<br />

maps. The SWIM/GRASS interface allows to extract<br />

spatially distributed parameters of elevati<strong>on</strong>, land use, soil

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