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Engineering Design of a Wastewater
UV Disinfection System
Karla Diviesti, Jess Dooley, Nick Tuttle, and Michael Lake
Clemson University, Clemson, SC
December 3, 2019
Outline
• Introduction
• Background
• Rationale
• Objective
• Approaches
• Literature Review
• Materials and Methods
• Results
• UV Wastewater Disinfection System
• Upstream Wastewater Components
• Recommendations
• Acknowledgements
Introduction
Background: Clemson University Wastewater Treatment
Plant (CUWWTP)
● 1.8 - 3.6 MGD current capacity
● Chlorination disinfection systems
○ Chlorine gas and dechlorination
sulfur dioxide
● Growing student population
○ 5000 in next 6 years
● Permits
○ New redundancy requirements
○ Difficult to expand
Student population expectancies
CUWWTP Primary Flow Chart
Influent
CUWWTP Site Visit
ReWa (Greenville, SC) Site Visit
ReWa (Greenville, SC) Site Visit
Rationale
● Increase student population
○ Projected growth to 26,300 in 2026
● Difficult to meet permit requirements without
downstream expansion
○ Contact time for chlorination
○ Increased level of redundancy required
● Increase safety
○ Adjacent to public walking path
○ Chlorine can be a harmful substance
○ Operator safety
● Decrease operation cost
The objective of this project is to engineer and design a UV
wastewater disinfection system to replace the current chlorine
gas based system at the Clemson University Wastewater
Treatment plant (CUWWTP).
Objective
Approaches
Task 1: To visit CUWWTP site
Task 2: To evaluate common UV disinfection systems and compare to the existing
chlorine gas system
Task 3: To evaluate E. coli and TSS in influent and effluent samples for both current
chlorine system at CUWWTP and proposed UV system
Task 4: To analyze influent and effluent flow data for an average daily flow and for high
flow events
Task 5: To create models of UV system
Task 6: To research and decide the type of UV lamp to use
Task 7: To investigate upstream components of the plant process
Task 8: To design a final UV disinfection process
Project
Disinfection
Technology
Wastewater
Engineering
Environmental Health
Interdisciplinary Connections
Literature Review
Literature Review Topics
● Methods of wastewater disinfection
● Types of UV lamps
● Types of UV systems
○ Open system
○ Closed system
○ Non-contact system
● Upstream components
○ Floating decanter
○ Sand filter
Wastewater Disinfection
Common Types of Disinfection
● Chlorine gas
● Chlorine dioxide
● Ozone
● Ultraviolet (UV) disinfection
Definition: The removal, deactivation, or killing, of pathogenic microorganisms
Chlorine Gas
● Chlorine gas and water react to create
hydrochloric acid and hypochlorous
acid (HOCl)
○ Cl2 + H2O HOCl + HCl
● Reaction lowers pH and alkalinity
● Dechlorination is required by sulfur
dioxide
○ SO2 +H2O H2SO3
○ H2SO3 +ClO2 +H2O 5H2SO4 +2HCl
Chlorine Dioxide
● Chlorine dioxide attacks the disulfide
bonds in RNA binding proteins
● Kills both inactive and active
organisms
● Difficult to store and transport
○ Onsite manufacturing
● Dechlorination is required
○ Sulfur dioxide
○ Sulfite salts
Ozone
● Ozone (O3) reacts with water to form
hydroxyl radicals (OH-1)
● The cell lyses and dies on interaction
with both ozone and hydroxyl radicals
● No regrowth of microorganisms
● Corrosive, requires corrosion-resistant
material
● Unwanted by-products
○ aldehydes, various acids, and aldo- and
keto-acids
Disinfection Kinetics: Chemical Treatment
● Chick-Watson Model
● Rennecker-Marinas Model
● Collins-Selleck Model
Ultraviolet Disinfection
● Non oxidizing process
● Disrupts DNA to inactivate
microorganisms
● Germicidal range: 200 nm - 300 nm
● Parameters for effectiveness
○ Chemicals present in wastewater
○ Total Suspended Solids (TSS) levels
○ Microorganisms present
○ Physical characteristics of UV system
● No harmful chemical byproducts
● Works against algae growth
Ultraviolet Disinfection
● UV light can also damage human DNA
● Water turbidity
● TSS concentration
● Microorganism reactivation
○ Repair damage done by UV exposure
○ Photoreactivation
○ Dark repair (nucleotide excision repair)
Disinfection Kinetics: UV Treatment
● UV disinfection - Modified Chick Watson
● UV Inhibition
○ Beer-Lambert Law
Types of UV Lamps
● Low pressure low intensity
○ UV-C (shortwave) ~ 254 nm
○ 80-85% monochromatic output
○ Optimal temperature (40℃) must be maintained
● Low pressure high intensity
○ Mercury-indium amalgam
○ More stability over wider temperature range
○ 2 to 10 times greater output than the low intensity lamps
● Medium pressure high intensity
○ Extremely high operation temperatures (600℃ - 800℃)
○ Between 20 to 50 times total UV-C output of low pressure low intensity
○ Efficiency issues, only 15-20% emission is within germicidal range
○ Large facilities limited space
UV System: Open System
● Low pressure, low or high intensity UV lamps
● Lamps are submerged parallel, perpendicular, or inclined
○ Inclined lamps can be longer with higher output
● Depth of flow needs to be maintained
○ Short circuiting
● Frequent cleaning of quartz sleeves
● Safety concerns
○ UV exposure during maintenance
UV System: Closed System
● Low or medium pressure, high
intensity UV lamps
● Can run both perpendicular and
parallel
● More complex hydraulics
UV System: Non Contact System
● UV lamps are not submerged in water
● Can be open or closed
● Can eliminate need for sleeves around
lamps
● Easier replacing/repairing of lamps
● Non-amalgam based lamps can be used
○ Low pressure low intensity
UV Lamp
Sleeve with water flow
Upstream Components:
Floating Decanter
● Remove water from the top of SBR
● Prevents sediment (TSS) in downstream processes
Cloth Disk Filter (CDF)
● Random weave membrane
● Several stacked flat, grooved discs
● Thickness depends on the influent flow
and desired effluent quality
● Requires backwashing for filter
cleaning
● Proven effectiveness for TSS removal
Upstream Components: Sand Filter
● Slow and rapid sand filtration
● Layered with sand and supporting
gravel
● Schmutzdecke or the “dirty layer”
○ Biological filtration layer
○ Slow sand filters only
● Better TSS removal
● Backwashing required to remove solids
and clean the filter
Effluent
Influent
Downstream Components: Flow Regulation
● Weir
○ Controls the depth within a channel
○ UV lamps must remain submerged at all
times
● Gate
○ Require mechanical operations
Materials and Methods
Materials and Methods
● Meetings with potential UV vendors
○ Enaqua and Trojan
● Site visits to current UV operating plants
○ ReWa
● Model of current infrastructure
○ SuperPro and Fusion
● Model of proposed UV installment
○ SuperPro and Fusion
○ Upstream component calculations
○ TSS
● Model of disinfection kinetics
○ Stella
● Cost analysis
Wastewater Quantity and Frequency
Current Flow Data
CUWWTP Wastewater Treatment/Quality and
Disinfection
● Chlorine process model – SuperPro
○ TSS evaluation
● SBR, secondary clarifier, chlorination, and dechlorination
Current Operating Cost
Chlorine
● 54 canisters
● $282.66/canister
Total: $15,263.64
Sulfur Dioxide Maintenance
Average Operating and Maintenance Cost per Year
● 38 canisters
● $107.45/canister
Total: $4,083.10
● Inspection and
annual repair
Total: $5,000.00
Total: $24,346.74
Recap UV vs. Chlorine Disinfection
● Non-chemical process
● No toxic byproducts introduced to the
environment
● Inactivates most bacteria, viruses, and
spores
● Equipment requires minimal space
● Low dosages may not effectively
inactivate microorganisms
● Effectiveness dependent on water
turbidity and TSS
● Dosing rates are flexible
● Effective against broad spectrum of
pathogens
● Requires chemicals for chlorination
and dechlorination
● Storage and handling of toxic
materials
● Byproducts are toxic to environment
UV Disinfection Chlorine Gas Disinfection
Why UV Disinfection?
● Effective at inactivating most microorganisms,
viruses, and spores
● Shorter contact time relative to other methods
● Eliminates the need to handle and store
toxic/dangerous chemicals
● No chemical byproducts harmful to humans or the
ecosystem
● Equipment requires less space than other methods
● Operator friendly
Design Inputs
Proposed System - Enaqua
Proposed System - Enaqua
Proposed System - Enaqua
Proposed System - Enaqua Front View
Proposed System - Enaqua Top View
Proposed System - Enaqua Inlet and Outlet View
Enaqua Initial Cost
$438,725.00
Enaqua Yearly Operating Cost
Lamps
● 41 lamps per year
● $100.00/lamp
Total: $4,100.00
Average Power Draw
Operating and Maintenance Cost per Year
● 0.117 $/kWh
● 207.84 kWh/day
Total: $8,875.81
$12,975.81
Possible Additional Maintenance - Enaqua
● Reactor cleaning 1-2 times per year
○ 5-10 total man hours
○ Clemson University facilities
Proposed System - TrojanUV
Proposed System - TrojanUV
Sample TrojanUV3000plus System - Texas
Proposed System - TrojanUV
TrojanUV Initial Cost
Total cost: $607,080.00
+ INSTALLATION
TrojanUV Yearly Operating Cost
Lamps
● 24 lamps per year
● $332.00/lamp
Total: $7,968.00
Average Power Draw Maximum Power
Draw
Operating and Maintenance Cost per Year
● 8760 Hour
● Power draw: 6.5 kW
● 0.117 $/kWh
Total: $6,701.84
● 8760 Hour
● Power draw: 16 kW
● 0.117 $/kW/h
Total: $16,496.83
Average: $14,669.84 Max:
$24,464.83
Possible Additional Maintenance
● Ballast replacement
○ 5 year warranty
○ $800 per ballast
○ 2% failure rate
● Acticlean Gel replacement
○ 2⨉ a year
○ $70 per year
● Wiper seal replacement
○ 2-3 years
○ $10 per module
○ 16 modules
○ $160 total
Results
CUWWTP Design Process- SuperPro
Chlorine process model – SuperPro
Current System Model- Fusion 360
Current System Model- Fusion 360
Pathogen Reduction Chlorine - Stella Model
● Chick-Watson Model
○ 15 mg/L Dose
Stella Model Results
● Contact Time 15-40 minutes
○ Log-5 reduction of E. coli
CUWWTP Design Process- SuperPro
Chlorine Process Design
UV Process Design Options- SuperPro
UV Process Design - with filter
UV Process Design - without filter
TSS Results - SuperPro
Current Disinfection
System
Designed Disinfection
System with filter
Designed Disinfection
System without filter
TSS Concentration
(mg/L)
TSS Concentration
(mg/L)
TSS Concentration
(mg/L)
Influent 170 170 170
Effluent 30 6 19
Input TSS Removal for
Operation
Input TSS Removal
for Operation
Input TSS Removal
for Operation
Floating Decanter N/A 75% 75%
Decanter 60% N/A N/A
Secondary Clarifier 55% 55% 55%
Filter N/A 70% N/A
Enaqua Model- Fusion 360
area for expansion
TrojanUV Model - Fusion 360
area for expansion
Pathogen Reduction UV - Stella Model
● Modified Chick-Watson Model
○ Dose of 40 mJ/cm^2
Stella Results
● Contact time 50-120 seconds
○ Log-5 reduction of E. coli
Alternative Designs Cost Comparison
f
TrojanUV Enaqua
● Channels, modules, power and
control panels
● Miscellaneous equipment
● Startup and commission
● UV reactor, power panels and
control panels
● Startup and commission
● Spare parts
Total: $607,080.00 Total: $438,725.00
Yearly Operating Cost Comparison
Current System Enaqua TrojanUV
● Chemical purchasing
● Maintenance
● Power usage
● Lamp replacement
● Power usage
● Lamp replacement
$24,346.74 $12,975.81 $14,669.84
Recommendations
● We recommend that an Enaqua non-contact
UV disinfection system be installed at the
CUWWTP
○ Roughly 50% reduction in operation cost
○ Increase operator and public safety
○ Easy expansion
○ Exceeds permit requirements
● In addition to the new system, we
recommend installing an upstream floating
decanter in the SBR
○ Increase TSS removal
○ If floating decanter becomes insufficient, add
choice of filter
Recommended Design
Initial Cost $438,725.00
Annual Operating
Cost
$12,975.81
Project Disinfection
Technology
Wastewater
Engineering
Environmental Health
Acknowledgements
We would like to thank the following people for their insights and contributions to this
project.
● Dr. Christophe Darnault and Ms. Jazmine Taylor
● Matt Garrison and the CUWWTP staff
● Gary Hunter and Black & Veatch Team
● Steve Squires (Enaqua)
● Michael Shortt (TrojanUV)
● Dr. Alessandro Franchi (AECOM)
● Bryan Kohert (ReWa)
Thank you!

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Engineering Design of a Wastewater UV Disinfection System

  • 1. Engineering Design of a Wastewater UV Disinfection System Karla Diviesti, Jess Dooley, Nick Tuttle, and Michael Lake Clemson University, Clemson, SC December 3, 2019
  • 2. Outline • Introduction • Background • Rationale • Objective • Approaches • Literature Review • Materials and Methods • Results • UV Wastewater Disinfection System • Upstream Wastewater Components • Recommendations • Acknowledgements
  • 4. Background: Clemson University Wastewater Treatment Plant (CUWWTP) ● 1.8 - 3.6 MGD current capacity ● Chlorination disinfection systems ○ Chlorine gas and dechlorination sulfur dioxide ● Growing student population ○ 5000 in next 6 years ● Permits ○ New redundancy requirements ○ Difficult to expand Student population expectancies
  • 5. CUWWTP Primary Flow Chart Influent
  • 9. Rationale ● Increase student population ○ Projected growth to 26,300 in 2026 ● Difficult to meet permit requirements without downstream expansion ○ Contact time for chlorination ○ Increased level of redundancy required ● Increase safety ○ Adjacent to public walking path ○ Chlorine can be a harmful substance ○ Operator safety ● Decrease operation cost
  • 10. The objective of this project is to engineer and design a UV wastewater disinfection system to replace the current chlorine gas based system at the Clemson University Wastewater Treatment plant (CUWWTP). Objective
  • 11. Approaches Task 1: To visit CUWWTP site Task 2: To evaluate common UV disinfection systems and compare to the existing chlorine gas system Task 3: To evaluate E. coli and TSS in influent and effluent samples for both current chlorine system at CUWWTP and proposed UV system Task 4: To analyze influent and effluent flow data for an average daily flow and for high flow events Task 5: To create models of UV system Task 6: To research and decide the type of UV lamp to use Task 7: To investigate upstream components of the plant process Task 8: To design a final UV disinfection process
  • 14. Literature Review Topics ● Methods of wastewater disinfection ● Types of UV lamps ● Types of UV systems ○ Open system ○ Closed system ○ Non-contact system ● Upstream components ○ Floating decanter ○ Sand filter
  • 15. Wastewater Disinfection Common Types of Disinfection ● Chlorine gas ● Chlorine dioxide ● Ozone ● Ultraviolet (UV) disinfection Definition: The removal, deactivation, or killing, of pathogenic microorganisms
  • 16. Chlorine Gas ● Chlorine gas and water react to create hydrochloric acid and hypochlorous acid (HOCl) ○ Cl2 + H2O HOCl + HCl ● Reaction lowers pH and alkalinity ● Dechlorination is required by sulfur dioxide ○ SO2 +H2O H2SO3 ○ H2SO3 +ClO2 +H2O 5H2SO4 +2HCl
  • 17. Chlorine Dioxide ● Chlorine dioxide attacks the disulfide bonds in RNA binding proteins ● Kills both inactive and active organisms ● Difficult to store and transport ○ Onsite manufacturing ● Dechlorination is required ○ Sulfur dioxide ○ Sulfite salts
  • 18. Ozone ● Ozone (O3) reacts with water to form hydroxyl radicals (OH-1) ● The cell lyses and dies on interaction with both ozone and hydroxyl radicals ● No regrowth of microorganisms ● Corrosive, requires corrosion-resistant material ● Unwanted by-products ○ aldehydes, various acids, and aldo- and keto-acids
  • 19. Disinfection Kinetics: Chemical Treatment ● Chick-Watson Model ● Rennecker-Marinas Model ● Collins-Selleck Model
  • 20. Ultraviolet Disinfection ● Non oxidizing process ● Disrupts DNA to inactivate microorganisms ● Germicidal range: 200 nm - 300 nm ● Parameters for effectiveness ○ Chemicals present in wastewater ○ Total Suspended Solids (TSS) levels ○ Microorganisms present ○ Physical characteristics of UV system ● No harmful chemical byproducts ● Works against algae growth
  • 21. Ultraviolet Disinfection ● UV light can also damage human DNA ● Water turbidity ● TSS concentration ● Microorganism reactivation ○ Repair damage done by UV exposure ○ Photoreactivation ○ Dark repair (nucleotide excision repair)
  • 22. Disinfection Kinetics: UV Treatment ● UV disinfection - Modified Chick Watson ● UV Inhibition ○ Beer-Lambert Law
  • 23. Types of UV Lamps ● Low pressure low intensity ○ UV-C (shortwave) ~ 254 nm ○ 80-85% monochromatic output ○ Optimal temperature (40℃) must be maintained ● Low pressure high intensity ○ Mercury-indium amalgam ○ More stability over wider temperature range ○ 2 to 10 times greater output than the low intensity lamps ● Medium pressure high intensity ○ Extremely high operation temperatures (600℃ - 800℃) ○ Between 20 to 50 times total UV-C output of low pressure low intensity ○ Efficiency issues, only 15-20% emission is within germicidal range ○ Large facilities limited space
  • 24. UV System: Open System ● Low pressure, low or high intensity UV lamps ● Lamps are submerged parallel, perpendicular, or inclined ○ Inclined lamps can be longer with higher output ● Depth of flow needs to be maintained ○ Short circuiting ● Frequent cleaning of quartz sleeves ● Safety concerns ○ UV exposure during maintenance
  • 25. UV System: Closed System ● Low or medium pressure, high intensity UV lamps ● Can run both perpendicular and parallel ● More complex hydraulics
  • 26. UV System: Non Contact System ● UV lamps are not submerged in water ● Can be open or closed ● Can eliminate need for sleeves around lamps ● Easier replacing/repairing of lamps ● Non-amalgam based lamps can be used ○ Low pressure low intensity UV Lamp Sleeve with water flow
  • 27. Upstream Components: Floating Decanter ● Remove water from the top of SBR ● Prevents sediment (TSS) in downstream processes
  • 28. Cloth Disk Filter (CDF) ● Random weave membrane ● Several stacked flat, grooved discs ● Thickness depends on the influent flow and desired effluent quality ● Requires backwashing for filter cleaning ● Proven effectiveness for TSS removal
  • 29. Upstream Components: Sand Filter ● Slow and rapid sand filtration ● Layered with sand and supporting gravel ● Schmutzdecke or the “dirty layer” ○ Biological filtration layer ○ Slow sand filters only ● Better TSS removal ● Backwashing required to remove solids and clean the filter Effluent Influent
  • 30. Downstream Components: Flow Regulation ● Weir ○ Controls the depth within a channel ○ UV lamps must remain submerged at all times ● Gate ○ Require mechanical operations
  • 32. Materials and Methods ● Meetings with potential UV vendors ○ Enaqua and Trojan ● Site visits to current UV operating plants ○ ReWa ● Model of current infrastructure ○ SuperPro and Fusion ● Model of proposed UV installment ○ SuperPro and Fusion ○ Upstream component calculations ○ TSS ● Model of disinfection kinetics ○ Stella ● Cost analysis
  • 33. Wastewater Quantity and Frequency Current Flow Data
  • 34. CUWWTP Wastewater Treatment/Quality and Disinfection ● Chlorine process model – SuperPro ○ TSS evaluation ● SBR, secondary clarifier, chlorination, and dechlorination
  • 35. Current Operating Cost Chlorine ● 54 canisters ● $282.66/canister Total: $15,263.64 Sulfur Dioxide Maintenance Average Operating and Maintenance Cost per Year ● 38 canisters ● $107.45/canister Total: $4,083.10 ● Inspection and annual repair Total: $5,000.00 Total: $24,346.74
  • 36. Recap UV vs. Chlorine Disinfection ● Non-chemical process ● No toxic byproducts introduced to the environment ● Inactivates most bacteria, viruses, and spores ● Equipment requires minimal space ● Low dosages may not effectively inactivate microorganisms ● Effectiveness dependent on water turbidity and TSS ● Dosing rates are flexible ● Effective against broad spectrum of pathogens ● Requires chemicals for chlorination and dechlorination ● Storage and handling of toxic materials ● Byproducts are toxic to environment UV Disinfection Chlorine Gas Disinfection
  • 37. Why UV Disinfection? ● Effective at inactivating most microorganisms, viruses, and spores ● Shorter contact time relative to other methods ● Eliminates the need to handle and store toxic/dangerous chemicals ● No chemical byproducts harmful to humans or the ecosystem ● Equipment requires less space than other methods ● Operator friendly
  • 42. Proposed System - Enaqua Front View
  • 43. Proposed System - Enaqua Top View
  • 44. Proposed System - Enaqua Inlet and Outlet View
  • 46. Enaqua Yearly Operating Cost Lamps ● 41 lamps per year ● $100.00/lamp Total: $4,100.00 Average Power Draw Operating and Maintenance Cost per Year ● 0.117 $/kWh ● 207.84 kWh/day Total: $8,875.81 $12,975.81
  • 47. Possible Additional Maintenance - Enaqua ● Reactor cleaning 1-2 times per year ○ 5-10 total man hours ○ Clemson University facilities
  • 48. Proposed System - TrojanUV
  • 49. Proposed System - TrojanUV
  • 51. Proposed System - TrojanUV
  • 52. TrojanUV Initial Cost Total cost: $607,080.00 + INSTALLATION
  • 53. TrojanUV Yearly Operating Cost Lamps ● 24 lamps per year ● $332.00/lamp Total: $7,968.00 Average Power Draw Maximum Power Draw Operating and Maintenance Cost per Year ● 8760 Hour ● Power draw: 6.5 kW ● 0.117 $/kWh Total: $6,701.84 ● 8760 Hour ● Power draw: 16 kW ● 0.117 $/kW/h Total: $16,496.83 Average: $14,669.84 Max: $24,464.83
  • 54. Possible Additional Maintenance ● Ballast replacement ○ 5 year warranty ○ $800 per ballast ○ 2% failure rate ● Acticlean Gel replacement ○ 2⨉ a year ○ $70 per year ● Wiper seal replacement ○ 2-3 years ○ $10 per module ○ 16 modules ○ $160 total
  • 56. CUWWTP Design Process- SuperPro Chlorine process model – SuperPro
  • 57. Current System Model- Fusion 360
  • 58. Current System Model- Fusion 360
  • 59. Pathogen Reduction Chlorine - Stella Model ● Chick-Watson Model ○ 15 mg/L Dose
  • 60. Stella Model Results ● Contact Time 15-40 minutes ○ Log-5 reduction of E. coli
  • 61. CUWWTP Design Process- SuperPro Chlorine Process Design
  • 62. UV Process Design Options- SuperPro UV Process Design - with filter UV Process Design - without filter
  • 63. TSS Results - SuperPro Current Disinfection System Designed Disinfection System with filter Designed Disinfection System without filter TSS Concentration (mg/L) TSS Concentration (mg/L) TSS Concentration (mg/L) Influent 170 170 170 Effluent 30 6 19 Input TSS Removal for Operation Input TSS Removal for Operation Input TSS Removal for Operation Floating Decanter N/A 75% 75% Decanter 60% N/A N/A Secondary Clarifier 55% 55% 55% Filter N/A 70% N/A
  • 64. Enaqua Model- Fusion 360 area for expansion
  • 65. TrojanUV Model - Fusion 360 area for expansion
  • 66. Pathogen Reduction UV - Stella Model ● Modified Chick-Watson Model ○ Dose of 40 mJ/cm^2
  • 67. Stella Results ● Contact time 50-120 seconds ○ Log-5 reduction of E. coli
  • 68. Alternative Designs Cost Comparison f TrojanUV Enaqua ● Channels, modules, power and control panels ● Miscellaneous equipment ● Startup and commission ● UV reactor, power panels and control panels ● Startup and commission ● Spare parts Total: $607,080.00 Total: $438,725.00
  • 69. Yearly Operating Cost Comparison Current System Enaqua TrojanUV ● Chemical purchasing ● Maintenance ● Power usage ● Lamp replacement ● Power usage ● Lamp replacement $24,346.74 $12,975.81 $14,669.84
  • 70. Recommendations ● We recommend that an Enaqua non-contact UV disinfection system be installed at the CUWWTP ○ Roughly 50% reduction in operation cost ○ Increase operator and public safety ○ Easy expansion ○ Exceeds permit requirements ● In addition to the new system, we recommend installing an upstream floating decanter in the SBR ○ Increase TSS removal ○ If floating decanter becomes insufficient, add choice of filter
  • 71. Recommended Design Initial Cost $438,725.00 Annual Operating Cost $12,975.81
  • 73. Acknowledgements We would like to thank the following people for their insights and contributions to this project. ● Dr. Christophe Darnault and Ms. Jazmine Taylor ● Matt Garrison and the CUWWTP staff ● Gary Hunter and Black & Veatch Team ● Steve Squires (Enaqua) ● Michael Shortt (TrojanUV) ● Dr. Alessandro Franchi (AECOM) ● Bryan Kohert (ReWa)

Editor's Notes

  1. KARLA
  2. KARLA
  3. KARLA
  4. Talk about site visit and emphasis on UV Increase amount of rationale Michael
  5. Michael Specifically mention that the red is following the water flow not the sludge
  6. Michael
  7. NICK Bryan Kohert
  8. NICK
  9. JESS Increased population will increase the number of decants in a day due to the increased amount of waste entering the system With that you need to maintain a certain contact time for chlorination which requires expanding the basin Costs money, requires permits that are difficult to obtain WWTP next to walking path can be harmful to enviornment and public if chlorine spills
  10. JESS
  11. KARLA
  12. Karla
  13. KARLA
  14. KARLA
  15. MICHAEL
  16. MICHAEL
  17. JESS Different from chlorine, does not hydrolyze in water The disulfide bonds in RNA binding proteins Proteins are prevented from being made Best way to store is as a liquid at 4C but can’t be stored for long because Chlorine gas dissociates into chlorine gas and O2 Hardly stored as gas as it can be explosive under pressure
  18. JESS
  19. MICHAEL Lower case where and insert deltaCW Put the other two equations in (rennecker-Marinas, Collins-Selleck Model)
  20. KARLA
  21. KARLA Chemicals and other microorganisms
  22. MICHAEL Fix the m/
  23. KARLA
  24. NICK
  25. Tkae out the a in the pdf screenshot NICK
  26. NICK Describe each picture, bottom left picture show that its a non-contact system
  27. JESS
  28. JESS
  29. Sand filter equation added, transport equations JESS
  30. NICK
  31. NICK
  32. Describe the picture MICHAEL Need to update this to match the followingm aterials and methods
  33. KARLA
  34. NICK
  35. NICK Matt garrison 5000
  36. MICHAEL
  37. MICHAEL
  38. KARLA DONT MOVE ANYTHING ON THIS SLIDE BECAUSE OF SMALL WHITE BOXES
  39. KARLA -make sure to state non-contact
  40. KARLA Cannot get the circles in the light bulbs
  41. KARLA 2 reactors in parallel both can handle 100% of the flow.
  42. KARLA
  43. KARLA
  44. JESS
  45. JESS
  46. JESS
  47. Make it about the design ? KARLA
  48. KAR:LA
  49. KARLA
  50. JESS
  51. JESS Fix to make less confusing Make the layout clearer Put the power of the same line
  52. JESS
  53. NICK
  54. NICK
  55. -Mention that you designed the 3D in Fusion -outer walls- 10.42’ -inner wall- 8’ NICK
  56. NICK Water- 4.67’ Inner walls- 8’ Outer Walls- 10.42’ Add inlet and outlet arrow
  57. MICHAEL
  58. MICHAEL
  59. NICK
  60. NICK
  61. NICK 170- based on design limits
  62. Flow depth- 2.524’ Reactor Length- 17.5’ Channel Width- 4.36’
  63. Depth- 3.83’ , Width- 1.33’ , Length 25’ 4 in Talk about potential for expansion (blocked off channels), lowering outlet weir, grates and UV modules
  64. MICHAEL Italicize E. coli
  65. MICHAEL
  66. KARLA
  67. KARLA
  68. JESS
  69. JESS
  70. JESS
  71. JESS
  72. JESS