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Viability of Heat Recovery from Combined Sewers
Mohamad Abdel-Aal PhD Researcher at the University of Bradford [email protected] R.Smits**, M. Mohamed*, K.De Gussem**, A. Schellart*, S Tait* *School of Engineering Design and Technology, University of Bradford, BD7 1PD, UK ** Department of Research, Aquafin, Dijkstraat 8, B-2630 Aartselaar, Belgium
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Structure
• What?
• Why?
• How? • Data
• Model
• Results
• Conclusions
• Future work
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What
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Heat loss
Distance = ?
Large temperature drop = Problems in WwTP
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Why
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• Over 500 wastewater heat pumps are in operation world-wide. Thermal ratings range from 10 kW to 20 MW.
• Sewage temperatures vary between 10 and 250C, in Europe, all year around
• In Switzerland; 6000 GWh of thermal energy are lost annually through the sewage system
UK Water Industry Energy
Breakdown
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5
How
Data
Analysis
Flow Rate
In-Sewer Temperatures Soil Temperatures
Model
Comparison to literature
Deterministic (Energy balance)
Daily variation pattern
Estimate distance required to compensate heat losses upstream
Predictive (Group method of data handling)
Pipe dimensions
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Data- Aquafin
• 6 Sites in Antwerp, Belgium
• Wastewater and in-sewer air temperatures, flow and soil measured every 20 minutes for 6 - 12 months
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Site
Average DWF Pipe length Pipe diameter
(m3/hour) (m) (m)
1 37 464 1.2
2 49 170 1.3
3 48 232 1.2
4 1000 1031 1.2
5 1100 1775 1.3
6 340 749 0.7
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Data- Analysis (July)
7 19.5
20.0
20.5
21.0
21.5
22.0
00:01 01:41 03:21 05:01 06:41 08:21 10:01 11:41 13:21 15:01 16:41 18:21 20:01 21:41 23:21
Tem
per
atu
re o
C
Time
Site 1 Upstream Site 2 Upstream Site 3 Upstream
Site 1 Downstream Site 2 Downstream Site 3 Downstream
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Data- Site 2
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Average WW temperature drop = 0.70 C or 40 C /km
1.50 C difference 21
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Data- Site 2
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Deterministic Model
10 𝒎𝒄𝒑 𝑻𝒋 − 𝑻𝒋+𝒏 = 𝒒𝒘𝒂 + 𝒒𝒘𝒔 + 𝒒𝒓𝒆𝒄𝒐𝒗𝒆𝒓𝒆𝒅
q= thermal energy w= wastewater, s= soil m=mass flow rate cp= thermal heat capacity
Tj Tj+n
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Deterministic Model
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𝒎𝒄𝒑 𝑻𝒋 − 𝑻𝒋+𝒏 = 𝒒𝒘𝒂 + 𝒒𝒘𝒔 + 𝒒𝒓𝒆𝒄𝒐𝒗𝒆𝒓𝒆𝒅
𝑞𝑤𝑎= 1
𝑅𝑤𝑎𝑇𝑤𝑎𝑡𝑒𝑟 − 𝑇𝑎𝑖𝑟 𝑞𝑤𝑠 =
1
𝑅𝑤𝑠𝑇𝑤𝑎𝑡𝑒𝑟 − 𝑇𝑠𝑜𝑖𝑙
Parameter Abbreviation Value in Feb Units
Thermal Resistivity between Wastewater and Air 𝑅𝑤𝑎 0.04 m2/0C
Thermal Resistivity between Wastewater and Soil 𝑅𝑤𝑠 0.5 m2/0C
Wastewater Temperature 𝑇𝑤𝑎𝑡𝑒𝑟 11.6 0C
In-Sewer Air Temperature 𝑇𝑎𝑖𝑟 9 0C
Soil Temperature 𝑇𝑠𝑜𝑖𝑙 9.5 0C
Mas flow rate m 14 Kg/s
Specific Heat Capacity for water cp 4.2 kJ/kg.0C
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Deterministic Model- Results
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y = 0.9248x + 1.45 R² = 0.998
y = 0.8619x + 2.77 R² = 0.992
y = 0.9555x + 0.93 R² = 0.989
y = 1.0478x - 0.22 R² = 0.998
y = 1.2014x - 1.94 R² = 0.995
y = 1.2734x - 2.57 R² = 0.997
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11
13
15
17
19
21
9 11 13 15 17 19 21
Mo
del
led d
ow
nst
ream
tem
per
atu
re 0
C
Measured downstream temperature 0 C
Site 1 Site 2 Site 3 Site 4 Site 5 Site 6
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Deterministic Model- Sensitivity Analysis
13 -80%
-30%
20%
70%
120%
170%
220%
270%
25% 50% 100% 200% 400%
Ch
ang
e in
do
wn
stre
am t
emp
erat
ure
Percentage of upstream temperature (100% = default value)
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Deterministic Model- Sensitivity Analysis
14 -0.8%
-0.4%
0.1%
0.5%
0.9%
1.3%
1.7%
2.1%
2.5%
25% 50% 100% 200% 400%
Ch
ang
e in
do
wn
stre
am t
emp
erat
ure
Percentage of default value (100% = default value)
In-sewer air temperature Ta
Pipe thermal conductivity, kp
Soil thermal conductivity , ks
Flow surface width, b
Soil depth, ds
Soil temperature, Ts
Wastewater flow rate, Q
Wastewater velocity, uw
Wetted perimeter, wet.p
Water soil thermal resistivity, Rws
Water air thermal resistivity, Rwa
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Predictive Model
• Group method of data handling
• Trained on Sites 1&2 for 6 Months Data (6,000 entries)
• Predicted for Sites 3, 4, 5 & 6 (20,00 entries)
15 Error = 9.4%
Error = 3%
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Predictive Model- Results (DWF )
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y = 0.9962x + 0.0836
R² = 0.994
y = 0.9956x - 0.4502
R² = 0.996
8.8
10.8
12.8
14.8
16.8
18.8
20.8
8.8 10.8 12.8 14.8 16.8 18.8 20.8
Mo
del
led d
ow
nst
ream
tem
per
atu
re
Measured downstream temperatures
Deterministic model Predective
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Deterministic Model- Application
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0
2
4
6
8
10
12
14
0 1 2 3 4 5 6 7 8 9
Do
wn
stre
am T
emp
erat
ure
, 0C
Sewer Length, km
Business As Usual, Q= 37 m3/h Soil In-Sewer Air
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Deterministic Model- Application
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0
2
4
6
8
10
12
14
0 1 2 3 4 5 6 7 8 9
Do
wn
stre
am T
emp
erat
ure
, 0C
Sewer Length, km
Business As Usual, Q= 37 m3/h 20 kW Heat Recovered, Q= 37 m3/h Soil In-Sewer Air
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Deterministic Model- Application
19
0
2
4
6
8
10
12
14
0 1 2 3 4 5 6 7 8 9
Do
wn
stre
am T
emp
erat
ure
, 0C
Sewer Length, km
Business As Usual, Q= 37 m3/h 20 kW Heat Recovered, Q= 37 m3/h250 kW Heat Recovered, Q= 37 m3/h SoilIn-Sewer Air
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Deterministic Model- Application
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0
2
4
6
8
10
12
14
0 1 2 3 4 5 6 7 8 9
Do
wn
stre
am T
emp
erat
ure
, 0C
Sewer Length, km
Business As Usual, Q= 37 m3/h 20 kW Heat Recovered, Q= 37 m3/h250 kW Heat Recovered, Q= 37 m3/h 500 kW Heat Recovered, Q= 37 m3/hSoil In-Sewer Air
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Model- Application
• Heat exchanger operating all year around
• 170kWh/m2 annual heat demand
• 100% heat exchanger efficiency
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Heat Exchanger Capacity
kW
Energy Recovered
MWh/yr
m2 heated
1,000 9 50
250,000 2,190 13,000
500,000 4,380 26,000
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Conclusions
• Data agrees with literature Schilperoort and Clemens (2009) and Hoes et al. (2009)
• Field measurements showed heat fluxes in sewers and hence there is potential for heat recovery
• Models showed R2 = 0.989 to 0.998
• Average errors are 0.3 and 0.40 C error for deterministic and predictive models respectively
• Simple predictive model- two parameters
• In-sewer air and upstream wastewater temperatures are key parameters
• Heat recovery has shown a potential in long sewer lines
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Future Work
• Model temperature drop along a Belgian sewer network using deterministic model (energy balance)
• Investigate the impact of transient deterministic model on modelling accuracy
• Test the model the model on more data
• Investigate further predictive techniques that incoperate sewer length
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References
• SEWAGE WATER: INTERESTING HEAT SOURCE FOR HEAT PUMPS
AND CHILLERS (Felix Schmid, Energy-engineer FH, SwissEnergy Agency for Infrastructure Plants Gessnerallee 38a, CH-8001 Zürich, Switzerland )
• Renewable energy potential for the water industry (Environment Energy Report: SC070010/R5)
• Heating energy consumption and resulting environmental impact of European apartment buildings (Constantinos A. Balaras*, Kalliopi Droutsa, Elena Dascalaki, Simon Kontoyiannidis)
• Schilperoort, R. P. and Clemens, F. 2009 Fibre-optic distributed temperature sensing in combined sewer systems. Water Science & Technology, 60. (5), 1127-1134.
• Hoes, O. A., Schilperoort, R. P., Luxemburg, W., Clemens, F. and Van de Giesen, N. 2009. Locating illicit connections in storm water sewers using fiber-optic distributed temperature sensing. Water Research, 43, 5187-5197.
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Thanks …
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