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Maps of the lowland river Sava

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Martin Baptist 1 , Marjolijn Haasnoot 1 , Guido van der Wedden 2<br />

en Huib de Vriend 2<br />

1 WL | Delft Hydraulics and 2 Delft University <strong>of</strong> Technology<br />

In co-operation with IAC, Ecorys, Alterra & RIZA


• Detention areas temporarily store water during floods, to alleviate<br />

flood risks downstream.<br />

• To work effectively, large areas are needed, preferably embanked and<br />

equipped with inlet and outlet structures (sluices).<br />

• Flood detention areas are considered along many European <strong>river</strong>s.<br />

• Flood management in <strong>the</strong> Central <strong>Sava</strong> Basin in Croatia is (already)<br />

largely controlled by flood detention areas.<br />

• In this study, <strong>the</strong> hydrological and ecological functioning <strong>of</strong> one <strong>of</strong><br />

<strong>the</strong>se detention areas, Lonjsko Polje, is studied to give advise on<br />

optimal ecological flood management and to learn from this existing<br />

situation.


Intake <strong>of</strong> <strong>the</strong><br />

SOS canal<br />

Odransko<br />

Polje<br />

1972: Trebež II<br />

outlet sluice<br />

Prevlaka inlet sluice<br />

Cesma <strong>river</strong><br />

1972 UN plan:<br />

Palanjek inlet<br />

weir<br />

Trebež I<br />

outlet sluice<br />

Dike


3650 1:100 year flood event<br />

(m3 2650<br />

/s)<br />

1000<br />

Est. storage capacity<br />

Present: 634·10 6 m 3<br />

1972 plan: 915·10 6 m 3<br />

A World Bank study concluded that<br />

for <strong>the</strong> 1972 plan <strong>the</strong> water levels <strong>of</strong><br />

floods will rise, <strong>the</strong> flood duration<br />

will double and <strong>the</strong>re will be more<br />

<strong>of</strong>ten high waters.<br />

max 600 in<br />

max 2370 in<br />

max 500 out + 250 out


• Main objective: Setting-up guidelines for <strong>the</strong> flood management <strong>of</strong><br />

<strong>the</strong> Lonjsko Polje area to combine (1) flood protection, (2) ecosystem<br />

development and (3) nutrient sink capacity. Compare different<br />

flooding scenarios.<br />

Expected results:<br />

• <strong>Maps</strong> <strong>of</strong> flood inundation depths, flood duration and time for<br />

evacuation for different flood events. Important for park<br />

management.<br />

• Assessment <strong>of</strong> <strong>the</strong> vegetation growth and succession for different<br />

flooding scenarios.<br />

• (Assessment <strong>of</strong> <strong>the</strong> nutrient trapping efficiency <strong>of</strong> Lonjsko Polje,<br />

important for <strong>the</strong> <strong>Sava</strong> nutrient load and subsequently <strong>the</strong> Danube<br />

load.)


• Hydrology: model <strong>the</strong><br />

flooding <strong>of</strong> Lonjsko Polje with<br />

<strong>the</strong> SOBEK overland flow<br />

module.<br />

• Ecology: assess <strong>the</strong><br />

vegetation structure and<br />

succession, related to<br />

flooding.<br />

• (Nutrients: assess <strong>the</strong><br />

nutrient balans <strong>of</strong> <strong>the</strong> Lonjsko<br />

Polje area by coupling <strong>the</strong><br />

flow model to a water quality<br />

model.)


Physical state<br />

Hydrology<br />

Present situation<br />

1972 plan with<br />

additional weir and<br />

sluice<br />

Mean year, 1997<br />

1: 100 year flood


• Peak discharge 3650 m 3 /s


!<br />

"#$!%<br />

!


& '<br />

• Contrary to <strong>the</strong> expectation,<br />

<strong>the</strong> flood duration for <strong>the</strong><br />

1972 plan is shorter than for<br />

<strong>the</strong> present situation.<br />

• This is due to <strong>the</strong> fact that<br />

water can leave Lonjsko Polje<br />

more easily via <strong>the</strong> new<br />

Trebež II sluice and Palanjek<br />

weir, as soon as <strong>the</strong> flood<br />

wave has past by.<br />

• Calculated storage capacity:<br />

Present: 613·10 6 m 3<br />

1972 plan: 845·10 6 m 3


Ecohydrological<br />

assessment<br />

SOBEK Vegetation map<br />

from <strong>the</strong> Park Service<br />

Flood duration<br />

- growing season<br />

- remaining part <strong>of</strong> year<br />

Knowledge rules<br />

give ecotopes after x years,<br />

based on flood duration,<br />

vegetation succession and<br />

management<br />

ecotope maps<br />

after x years<br />

Ecotope map


( ' '<br />

Flood event knowledge rules Season inundation (days) Succession in years<br />

Ecotope code site factor flooding Nov-Mar Apr-Jun 2 10 20 50 100<br />

dry hardwood forest 101 dry < 20 d/yr 20 10 301 201 201 101 101<br />

hardwood forest 102 dry-moist 20 - 50 d/yr 50 20 301 201 201 102 102<br />

aspen plantation 601 moist 50-100 d/yr 100 20 301 201 201 102 102<br />

s<strong>of</strong>twood forest 103 moist 50 - 150 d/yr 120 90 302 202 104 104 105<br />

wet hardwood forest 105 moist-wet 50 - 150 d/yr 120 90 302 202 104 104 105<br />

wet s<strong>of</strong>twood forest 104 wet 50 - 150 d/yr 120 90 302 202 104 104 105<br />

marsh forest 106 wet > 150 d/yr 120 90 303 303 106 106 106<br />

hardwood shrub 201 moist-wet < 50 d/yr 50 20 301 201 201 102 102<br />

s<strong>of</strong>twood shrub 202 wet 50 - 150 d/yr 120 90 302 202 104 104 105<br />

herbaceaous rough 301 dry < 20 d/yr 20 10 301 201 201 101 101<br />

wet herbaceous rough 302 moist > 50 120 50 302 202 104 104 105<br />

herbaceous swamp 303 wet > 150 d/yr 120 50 303 303 106 106 106<br />

reed swamp 304 wet-water 365 d/yr 120 30 701 304 304 304 304<br />

moist meadow 502 moist 20 - 50 d/yr 50 20 301 201 201 102 102<br />

floodplain hayfield 401 moist 20 - 50 d/yr 50 20 301 201 201 102 102<br />

wet hayfield 402 wet 50 - 150 d/yr 120 50 301 202 104 104 105<br />

wet meadow 503 wet 50 - 150 d/yr 120 50 302 202 104 104 105<br />

wet natural pasture 504 wet 50 - 150 d/yr 120 50 302 202 104 104 105<br />

wet grassland 505 wet > 150 d/yr 120 50 302 302 106 106 106<br />

meadows and agriculture 501 < 20 d/yr 20 10 301 201 201 101 101<br />

arable floodplain moist 20 - 50 d/yr 50 20 301 201 201 102 102


Physical state<br />

Hydrology<br />

Current situation<br />

1972 plan with<br />

additional weirs and<br />

sluices<br />

Mean year, 1997<br />

1: 100 year flood


& '<br />

• The effects <strong>of</strong> a 1:100 year flood event differ mainly along<br />

<strong>the</strong> borders <strong>of</strong> <strong>the</strong> central Lonjsko Polje region. Contrary to<br />

<strong>the</strong> expectation, <strong>the</strong> 1972 plan is favourable. The shorter<br />

flood duration leads to less severe effects.<br />

• The mean, autonomous succession differs as well for both<br />

scenarios. However, results show that nature management<br />

is a more important factor for vegetation succession than<br />

flood duration.


• A 1:100 year flood event will inundate <strong>the</strong> entire Lonjsko<br />

Polje within two weeks time, <strong>the</strong>refore all lifestock has to be<br />

evacuated in time.<br />

• The flood duration time <strong>of</strong> floods in Lonjsko Polje is not<br />

determined by <strong>the</strong> amount <strong>of</strong> water that goes in, but by <strong>the</strong><br />

amount <strong>of</strong> water that can go out.<br />

• The ecological effects <strong>of</strong> a flood event are large,<br />

irrespective <strong>of</strong> <strong>the</strong> execution <strong>of</strong> <strong>the</strong> 1972 plan.<br />

• It is recommended to consider an in- and outlet structure<br />

that can take in water during dry summer periods and can<br />

discharge water to drain <strong>the</strong> filled detention area faster.

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