Optimizing a Pure Oxygen WWTP

Optimizing a Pure Oxygen
Wastewater Treatment Plant
Randal W. Samstag, PE, BCEE
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Principal Technologist
Outline
• HPO Basics
• HPO Upgrade Case Studies
– West Point WWTP Pilot Plant
– Bellingham Post Point WWTP
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• Conclusions
2
The High Purity Oxygen (HPO) Process
• Invented by Union Carbide Corp. in early 1970s
• “High Purity Oxygen”
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– Cryogenic Plant (95 – 99%)
– Pressure Swing Adsorption (88 – 93%)
– Vacuum Swing Adsorption (88 – 93%)
3
HPO Upgrade Case Studies
• West Point WWTP HPO Pilot Plant
• Bellingham Post Point WWTP
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– HPO Modifications Project
– Nitrogen Removal Upgrades
4
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West Point WWTP
Pilot Plant
5
West Point HPO Test Facility
• 4-stage HPO pilot facility (Lotepro)
– 20-30 gpm
– SRT: 1-2 days
• Mar - Dec 1988
• 3 modes evaluated:
– Plug Flow
– Contact/Reaeration
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– Anaerobic Selector w/ Plug Flow
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HPO Test Facility Schematic
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7
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SVI, mL/g
Settleability Data from HPO Test
Facility
900
800
700
600
500
400
300
200
100
0
Min
Ave
Max
8
The Culprits
• Microscopic evaluation
found filaments
– Thiothrix II
– Type 021N
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• Sulfur oxidizing aerobes
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Influence of SRT and Temp on PAO
Washout Aerobic SRT (Days)
Nitrifier Washout
PAO Washout
14
12
10
EBPR and Nitrification
8
6
EBPR
4
2
No EBPR
0
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Nocardia Washout
10
15
20
25
30
Temperature (Degrees C)
Mammais and Jenkins, 2001
PAO Have Higher Floc Density
• PAO form Neisser-positive
cell clumps
• Compact flocs settle faster
than highly filamentous
sludges
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• Bio P organisms have a
higher density than typical
zoogleal or filamentous
organisms
Schuler and Jang, 2007
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Bellingham Post
Point WWTP
12
The Bellingham Post Point WWTP
• 20 mgd capacity HPO
activated sludge plant
• 10 ton/day pressure swing
absorption HPO system
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• Three HPO basin stages
Settleability History
• Average SVI of 170 mL/g from 1999 to 2004
• Filament caused settleability problems
– Type 1701 (Low DO)
– Type 1863 (Low SRT)
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• Periodically high VFA feed from influent sewer and
from solids dewatering operation 3-4 days per week
leading to slime bulking
14
Idea for Improvement – Anaerobic
Selector
• Provide zone for uptake of VFA
• Encourage growth of phosphorus accumulating
organisms (PAO)
• Increasing population distribution of PAO increases floc
density
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• PAO have a compact morphology and higher density than
other typical activated sludge bacteria (Schuler and
Jenkins)
• Experience at three other HPO plants (SE Essex SD,
Hyperion, SE San Francisco)
15
The HPO Modifications Project
• Improve settleability by converting first stage to
anaerobic selector
• Replace aerators to improve oxygen transfer
• Add variable speed drives to mixers to improve
control and save power
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• Selectors added capacity for interim operation until
major capacity upgrade could be completed
16
SVI History Before and After Conversion
to Anaerobic Selector
Comparison of SVI and MCRT
350
3.5
Aerobic
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3.0
250
2.5
200
2.0
150
1.5
100
1.0
50
0
07/17/05
Anaerobic
SVI 7/Avg ml/g
12/14/05
0.5
MCRT 7/Avg Days
05/13/06
10/10/06
03/09/07
08/06/07
01/03/08
0.0
06/01/08
MCRT (Days)
SVI (mL/g)
300
The Original Aerators
• Conventional conically
shaped low speed
aerators with bottom
impellors
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• Estimated standard
aerator efficiency (SAE) 3.2 pounds of oxygen per
hour per horsepower
New Aerators
• m2t Technologies
• Flat-bladed surface
aerators without bottom
impellers
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• Initial estimate of SAE
(second stage conditions)
– 4.0 pph/hp
Low Speed Testing for First Stage
Aerators
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• Tested to deliver
0.5 ft per second velocity
at the bottom of the test
tank at low speed in first
stage (anaerobic /
aerobic)
High Speed Testing
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•
Test-tank tested
at approximately
3.9 pph/hp under
high speed conditions
simulated for second
stage
Simulation of Variable Speed Control
• Savings only occur when
aerators are under-loaded
16
Dissolved Oxygen Concentrations (mg/L)
• Simulations by Michael
Stenstrom of UCLA
indicated up to 35%
savings in power with VSD
control
14
DO1
DO2
DO 3
12
10
8
6
4
2
0
5
10
15
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Time (hours)
20
25
Summary Comparison Performance
Description
Aerobic (2006)
Anaerobic (2007)
Difference (%)
7.2
6.7
-6.8%
1,291
1,212
-6.5%
1.21
1.15
-5.7%
155.71
126.77
-22.8%
Estimated Mixer
Power (hp)
222.2
125
-77.9%
Estimated Oxygen
Power (hp)
215.2
201.6
-6.8%
Estimated Total
Power (hp)
437.5
326.6
-34.0%
O2 (tpd)
O2 (lb/mgal)
O2 (lb/lb BOD)
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SVI (mL/g)
Project Budget
• Total cost - $670,000
• Puget Sound Energy grant - $330,000
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• City of Bellingham cost - $340,000
24
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Comparison of Operating Modes
Actual Bellingham Operation
Anaerobic Selector
Operation - 2007
HPO Operation - 2006
• 100% Aerobic
• 67% Aerobic
• 2.2 Days Aerobic SRT
• 1.6 Days Aerobic SRT
• 157 mL/g SVI
• 126 mL/g SVI
• 2,400 mg/L MLSS
• 2,900 mg/L MLSS
25
Comparison of Operating Modes
Actual Bellingham Capacity
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HPO Operation - 2006
20 MGD Capacity
Anaerobic Selector
Operation - 2007
22 MGD Capacity
10 Percent Increase
26
What About BNR Conversions?
• Concerns about HPO
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– CO2 accumulation -> low pH -> suppresses
nitrification
– As SRT increases HPO becomes less and less
economical compared to fine bubble
– Examples:
•
•
•
•
•
LOTT (Olympia, Washington)
Denver Metro
Indianapolis
Bellingham
All abandoned HPO for BNR
27
Oxygen Supply Cost as function of SRT
HPO: New VPSA HPO Plant
AAS: New Diffused Aeration System
$800
$700
Unit Cost of Oxygen ($/ton)
$600
$500
$400
$300
$200
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$100
$0
1.5
2.5
SRT (Days)
8.0
28
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HPO Conclusions
29
Conclusions from the HPO Test Facility
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• Anaerobic selectors at the HPO test facility failed
because low SRT, low temperature prevented
formation of an environment supportive of EBPR.
PAO were washed out.
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30
Conclusions from the Post Point Project
• Anaerobic selector provided a way to control settleability
by encouraging PAO and taking up excess VFA
• Improved oxygen transfer efficiency of new aerators
saved power
• Variable speed control of DO provided power savings and
improved process control
• The upgrade provided a 10 Percent capacity increase for
interim operation
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• For BNR upgrade, fine bubble was more economical
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Thank you!
Questions?
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Randal Samstag
[email protected]
206-684-6532 (office)
206-851-0094 (mobile)
Generalized Conclusions about HPO
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The Initial Claims
Experience
• Less O2 consumption
• O2 consumption depends more on
SRT than on DO
• Better settling sludge
• Little evidence of better settleability
at a given SRT
• Can operate at a higher MLSS
• If settling is not better, no
justification for higher MLSS
• Smaller tank volume required
• If settling is not better, no
justification for smaller tanks
• More power efficient than
conventional aeration
• Power efficiency depends on SRT
• Can be used for nitrification
• High CO2 decreases pH and inhibits
nitrification
33
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MLSS Showed Indications Phosphorus
Accumulating Organisms
34
Recent SVI and SRT Data from West
Point WWTP
West Point SVI and SRT Data
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SRT (day)
Linear (SVI)
30 per. Mov. Avg. (SVI)
30 per. Mov. Avg. (SRT (day))
Linear (SRT (day))
450
9.0
400
8.0
350
7.0
300
6.0
250
5.0
200
4.0
150
3.0
100
2.0
50
1.0
0
12/4/05
12/4/06
12/4/07
12/3/08
12/3/09
SRT (Days)
SVI (mL/g)
SVI
0.0
12/3/10
35
Summary Comparison
Operation
Description
Aerobic
(2006)
Anaerobic
(2007)
Difference (%)
Flow (mgd)
12.2
12.1
-0.8%
BOD (ppd)
12,852
12,994
1.1%
1,763
2,057
14.3%
Total SRT(days)
2.2
2.4
6.5%
Aerobic SRT (days)
2.2
1.6
-40.3%
13.3
7.4
-78.8%
Temp (Deg C)
17.57
17.24
-1.9%
O2 Purity (%)
88%
89%
1.4%
MLSS (mg/L)
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DO (mg/L)
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Comparison of Operating Modes
Typical Operating Assumptions
Classical HPO Operation
• 100% Aerobic
Anaerobic Selector
Operation
• 85% Aerobic
• 1.5 Days Aerobic SRT
• 2.5 Days Aerobic SRT
• 200 mL/g SVI
• 120 mL/g SVI
• 1,700 mg/L MLSS
• 2,200 mg/L MLSS
37
Comparison of Operating Modes
Capacity Impact
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Classical HPO Operation
13 MGD Capacity
Anaerobic Selector
Operation
17 MGD Capacity
30 Percent Increase
38