Comparison of technology, costs and
environmental benefit of wastewater treatment plants in mountainous areas in the alps
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Stuttgart Refuge

Site description and boundary conditions
Design and treatment efficiency

Site description and boundary conditions


boundary conditions

maximum daily organic load [PE]
150
maximum hydraulic load [m3/d]
10
annual organic load [kg BOD/a]
400
altitude [m a.s.l.]
2319
sensitivity [hydrogeology, protected area ...] limestone
lagal requirements [BOD elimination]
80%
operation period [season]
summer
energy supply [type, kW]
grid
means of transport [type]
supply cable car
existing WWTP [type, condition, volume l/PE]
3-chambers, good condition, 223



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Fig. 4.41: Flow-scheme of the WWTP Stuttgart Refuge


Abb. 4.42
Abb. 4.42:Installation of a separate kitchen wastewater pipe and the PE-grease trap.


Abb. 4.43
Abb. 4.43: Upgrading of the existing 3-chambers septic tank to a cyclic activated sludge system (typical alpine weather conditions).


Design and treatment efficiency

Loading of the biological treatment

WWTP Stuttgart Refuge
seasonal average
max. week 
max. day
loading [EW40]
56
118
150
BOD5-load [kg/d]
2.2
4.7
6.0
influent flow Q [m3/d]
3.9
7.3
10.0

 

Design according to the F/M ratio in the max. week

V =  20 m3 (volume tank)

Maerob = 20 m3 x 3.3 kg SS/m3 x (13.4/24) = 36.9 kg SS (aerobic sludge mass)

BSS = 4.7 kg BOD5 /d / 36.9 kg SS = 0.13 kg/kg.d (aerobic sludge loading)

OB = 4.7 x 3 kg O 2 /kg BOD5 / 24 h = 0.6 kg O2/h (oxygen demand)



Energy demand

max. power
[W]
max. electric work
[kWh/d]
mean electric work
[kWh/d]
1.200
16
12


Treatment efficiency

date
[dd.mm.yyyy]
CODeffluent
[mg/l] 
NH4-N effluent [mg/l] 
NO3-N effluent [mg/l]
CODelimination [%]
Nelimination [%]
loading
[% of PEmax ]
06.08.1999
155
93
5,6
87
44
61
04.08.2000
85
84
2,2
94
15
12 
21.09.2001
100
86
17
95
39
4


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28. Mar 2002