Power Plants in northern Germany – Project Oliver Stoschek

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Power Plants in northern Germany – Project
examples for optimizing intakes and outfalls
Oliver Stoschek
DHI – Coastal Engineering
Head of branch office, DHI-WASY Germany
Agenda
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Scope
Method
Coastline Example - Wilhelmshaven
Brackish Environment – Brunsbüttel
Tidal River – Stade
Summary
01.
Scope
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Scope
• EIA for 15 Power Plants from 2006 to 2012
EIA criteria (Heat Capacity Plan):
ΔT < 3K @ max. 500m radius,
3K < 25% cross section,
T < 28°C (peak 30°C),
< 0.3 m/s at intake (fish)
>80% oxygen at outfall
must be fulfilled.
• Only 2 locations are realised
Adaption of local structures
to optimize costs.
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02.
Method
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Method
Proof the setup – revise the setup – proof it again
• Numerical 3-D models were used (MIKE3 & Ecolab & Particle
Tracking & Sediment & Transport – DHI, OpenFoam (CFD))
• Worst case situations were studied:
summer time, characterized by high temperatures and low upstream
discharge (as far as applicable)
Optimize the layout to stay
within the EIA criteria and have
an optimised output
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Method / Location
1. Wilhelmshaven can be found at the German
coastline without any influence from upstream
discharges.
2. Brunsbüttel is located in the estuary of the
River Elbe, a specific brackish environment
with 3-dimensional currents.
3. Stade is located inside the Elbe River in a
tidal environment. It is dominated by tides and
upstream discharge. Low oxygen content and
nature reserve areas are driving the design.
All examples: tidal range up to 4m
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03.
Coastline Example - Wilhelmshaven
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Wilhelmshaven
• Longshore current
• Existing plant near by
• … and a new port
-> no longshore current
-> additional sedimentation
• Optimize the position of the outfall to obtain
the least impact on the existing plant and
minimize the recirculation (MIKE 3)
• Assess sediment transport (MT/ST)
• Optimize the intake (CFD)
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Model Area
Wilhelmshaven
30 m³/s @ ΔT of 7K
-> Position 3 was chosen
Pos. 1 has higher impact
on neighboring plant
Pos. 4 and 5 have an
significant impact on
recirculation
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Optional Locations
Wilhelmshaven
A diffusor was chosen as a first choice
-> High sedimentation occurs
-> New solution needed
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Diffusor
Wilhelmshaven
• A single point outfall was chosen
• The intake design was optimised (<0.3m/s)
Outfall
Intake
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Wilhelmshaven
mean temperature increase
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max temperature increase
04.
Brackish Environment – Brunsbüttel
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Brunsbüttel
• Longshore current > 1.5 m/s
• Existing plants near by
• Optimize the position of the
outfall to obtain the least impact
on the existing plants and
minimize the recirculation
(MIKE 3)
• Deliver long term 3D-HD data
for a habitat model (1 year)
Mittelwert
mean
• Impact on O2 (Ecolab)
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Model Area
Temperature (July/August) near bottom
Wassertemperatur [°C]
2002
2003
2004
2005
2006
20.3
21.2
19.6
19.6
22.1
minimum
Minimum
17.0
18.0
16.7
17.5
18.9
maximum
Maximum
23.6
24.7
22.8
21.4
25.2
Brunsbüttel
Intake upstream or downstream?
• 40.000m³/s tidal discharge
• full vertical mix of cooling water in
riverine water
intake downstream, outfall upstream
(1b)
• Less impact on NPP
• Less recirculation (deeper water)
• No EIA criteria will be violated
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Temperature increase ΔT (K)
Brunsbüttel
Location / Variant
Max.
Mean
Intake NPP Var. 1a
2.4
0.4
Intake NPP Var. 1b
1.0
0.3
Intake SWS Var. 1a
1.3
0.4
Intake SWS Var. 1b
0.9
0.3
Temperature increase (vertical average) at the planned SWS coal fired power
plant (CFPP) in Brunsbüttel (variant 1b)
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Brunsbüttel
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05.
Tidal River – Stade
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Stade
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No significant longshore current
Low O2 values
Nature reserve area near by
6.000m³/s tidal discharge / 150
to 3.500m³/s river discharge
• Pier is blocking cross currents
• Optimize the position, water
deth and length of the pier to
stay in EIA criteria (MIKE 3)
• Impact on O2 (Ecolab)
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Stade
Current speed during flood
period at the surface
Current speed during ebb period
at the surface
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Stade
maximum exceedance of
3°C excess temperature
(sliding 6 hour mean value)
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06.
Summary
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Summary
• Three examples for intake and outfall designs at the northern
German coast were shown.
• Each example was adapted to the local situation. Numerical 3D
hydraulic models were used to optimize the shape, size and location
of the structures.
• All examples show the clear demand of on-site investigations to
optimize the design for intake and outfall structures
– not one design for all, not only heat is driving the design.
• In all shown cases optimization was needed to stay within the
environmental criteria, e.g. the size of the mixing zone
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Thank you
Oliver Stoschek
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