Download presentation
Presentation is loading. Please wait.
Published byMagnus Fields Modified over 9 years ago
1
1 JCI 1 1 Energy can be neither created nor destroyed, but only converted from one form to another. First Law of Thermodynamics Karl Friedrich Mohr In a closed system the mass of the system must remain constant over time. Law of Conservation of Mass Antoine Lavoisier
2
2 CEE 426 Wastewater Treatment Plant Design October 23, 2013 12:05 pm Room 1213 Engineering Hall Thomas E. Jenkins President JenTech Inc. 6789 N. Elm Tree Road Milwaukee, WI 53217 414-352-5713 tom.jenkins.pe@gmail.com
3
3 Calculating Air Rates Types of Aerators and Processes Blower Selection Aeration and Energy 3
4
4 Aeration is the Most Significant Energy Use in a WWTP Aeration and Energy 4
5
5 5 Rates vary with: Time of Day On-peak, Off-Peak Day of Week Size of Costumer Demand (kW) and Consumption (kWh) The First Goal of an ECM (Energy Conservation Measure) is to Reduce Cost Energy Consumption ≠ Energy Cost
6
6 6 BOD Removal Oxygen Required for metabolism Amount of O 2 is proportional to Organic Load Utilization Approximately 1.1 lb. O 2 /lb BOD 5 Types of Processes
7
7 7 Nitrification NH 3 NO 3 Oxygen Required to convert Ammonia to Nitrate Amount of O 2 is proportional to Ammonia Concentration Utilization 4.6 lb. O 2 /lb NH 3 Converted Hydraulic Residence Time and SRT (Solids Retention Time) Determine if Nitrification Will Occur Types of Processes
8
8 8 Denitrification NO 3 N 2 and O 2 Anoxic Reaction Carbon Source Required Approximately 25% of O 2 Used for Nitrification Can be Recovered Only if raw wastewater is used as carbon source Types of Processes
9
9 9 Mechanical Fine Pore Coarse Bubble Jet Aeration All work by creating contact between air and the mixed liquor. All require the transfer of mass across the liquid/gas boundary. Types of Aerators
10
10 Horizontal Mechanical Aerator (Brush Aerator) Mechanical Aerators 10
11
11 Vertical Shaft and Aspirating Mechanical Aerator Mechanical Aerators 11
12
12 Calculating O 2 Transfer Typical aerator SOTR 2.0 to 4.5 lbO 2 /hp-hr
13
13 Determining Power Required for Mechanical Aerators: Calculating Air Rates and O 2 Transfer Note that hp USED is a function of design! Mixing Limits: 1 ft/sec velocity 0.5 hp/1,000 ft 3
14
14 Proportional to Immersion Reduced Immersion < OTR and < hp Variable Weir Level Control Proportional to Speed Lower Speed < OTR and < hp Variable Frequency Drives, Two Speed Motors Proportional to Actual DO Concentration Lower is Better DO Control Significant Mechanical Aerator Energy
15
15 Mechanical Aerator Energy Lower speed = lower power
16
16 Mechanical Aerator Energy Lower speed = lower oxygen transfer
17
17 Mechanical Aerator Energy Net result is lower efficiency Does It Matter?
18
18 Coarse Bubble Diffused Aeration
19
19 Fine Pore (Fine Bubble) Diffused Aeration
20
20 Calculating OTE and O 2 Transfer
21
21 Calculating Air Flow Rates
22
22 Proportional to Submergence Deeper is Better Also Requires Higher Blower Power Proportional to Air Flow per Diffuser Flux Rate (1 to 10 SCFM/ft 2 Typical) Lower is better Proportional to Actual DO Concentration Lower is Better DO Control is Significant Diffused Aeration Energy
23
23 Calculating Air Rates and OTE Typical OTE f ≈ 50% SOTE SOTE Fine Pore ≈ 2% per foot submergence SOTE Coarse Bubble ≈ ¾ % per foot submergence Mixing Limits: Fine Pore: 0.12 to 0.08 CFM/sq ft Coarse Bubble: 20 CFM/1,000 cu ft
24
24 OTE Increases with Higher Submergence OTE Decreases with Higher Air Flow per Diffuser Diffused Aeration 7.6m = 25’ 6.1m = 20’ 4.6m = 15’ 3.0m = 9.8’ 1.5m = 5’ 1m 3 /hr = 0.58 CFM 5m 3 /hr = 2.94 CFM 9m 3 /hr = 5.30 CFM
25
25 Excess DO means significantly more aeration power. Diffused Aeration
26
26 Miscellaneous Aeration Processes Aerobic Digestion Sludge Holding Post-Aeration Channel Aeration and Equalization Types of Processes
27
27 Energy use varies with time of day OTE, α, Organic Load, Hydraulic Load, All Vary with Time of Day Aeration and Energy 27
28
28 Efficiency Control Turndown Design Parameters Blower Selection Considerations
29
29 Efficiency Varies with Blower Type Range is 60% to 80% Aeration and Energy 29
30
30 Blower Power is a Function of Pressure and Flow Rate Efficiency Varies Flow Rate for a Given Blower Efficiency Drops as Flow is Decreased Good Turndown (>50%) is Desirable Aeration Blower Power 30
31
31 Aeration Blower Power 31
32
32 Aeration Blower Power Ignoring Relative Humidity
33
33 Aeration Blower Power
34
34 Aeration Blower Power Blower System Q max :Q min = 8:1 Specify Blower System for Turndown Four with Design Flow at 33% Max Q Two with Design Flow at 50% Max Q Plus Two with Design Flow at 25% Max Q 50% Turndown Each Blower
35
35 Design Specifications Identify Worst Case Operating Conditions For Discharge Pressure Max Temperature Max Relative Humidity Max System Flow Rate and ΔP For Motor Power For Throttled Centrifugal bhp at Min Temperature For Variable Speed Centrifutal bhp at Max Temperature Evaluation Conditions do not Equal Design Conditions Aeration Blower Power 35
36
36 Process Requirements Come First! Systems should be justified by payback Aeration and Energy 36
37
37 Over Life of Equipment: Energy Cost is more Significant than Equipment, Installation, or Maintenance Costs Aeration and Energy 37
38
38 http://www.sanitaire.com/3117803.asp http://www.stamfordscientific.com/ http://www.wastewater.com/ http://www.eimcowatertechnologies.com/ http://www.water.siemens.com/en/about_us/legacy_bra nds/Pages/envirex.aspx http://rootsblower.com/ http://water.epa.gov/scitech/wastetech/upload/Evaluatio n-of-Energy-Conservation-Measures-for-Wastewater- Treatment-Facilities.pdf Internet References
39
39 Aeration and Energy Questions? 39
Similar presentations
© 2025 SlidePlayer.com. Inc.
All rights reserved.