Coefficient of Thermal Expansion and their Importance.pptx
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
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
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
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)
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
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
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
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
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
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
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)
Talk about site visit and emphasis on UV
Increase amount of rationale
Michael
Michael
Specifically mention that the red is following the water flow not the sludge
Michael
NICK
Bryan Kohert
NICK
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
JESS
KARLA
Karla
KARLA
KARLA
MICHAEL
MICHAEL
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
JESS
MICHAEL
Lower case where and insert deltaCW
Put the other two equations in (rennecker-Marinas, Collins-Selleck Model)
KARLA
KARLA
Chemicals and other microorganisms
MICHAEL
Fix the m/
KARLA
NICK
Tkae out the a in the pdf screenshot
NICK
NICK
Describe each picture, bottom left picture show that its a non-contact system
JESS
JESS
Sand filter equation added, transport equations
JESS
NICK
NICK
Describe the picture
MICHAEL
Need to update this to match the followingm aterials and methods
KARLA
NICK
NICK
Matt garrison 5000
MICHAEL
MICHAEL
KARLA
DONT MOVE ANYTHING ON THIS SLIDE BECAUSE OF SMALL WHITE BOXES
KARLA
-make sure to state non-contact
KARLA
Cannot get the circles in the light bulbs
KARLA
2 reactors in parallel both can handle 100% of the flow.
KARLA
KARLA
JESS
JESS
JESS
Make it about the design ?
KARLA
KAR:LA
KARLA
JESS
JESS
Fix to make less confusing
Make the layout clearer
Put the power of the same line
JESS
NICK
NICK
-Mention that you designed the 3D in Fusion
-outer walls- 10.42’
-inner wall- 8’
NICK
NICK
Water- 4.67’
Inner walls- 8’
Outer Walls- 10.42’
Add inlet and outlet arrow