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09/14/06. B
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1. Toledo Waterways Initiative and 185 mgd HRT FacilityWet Weather Partnership CSO WorkshopChicago, IL Larry Jaworski - Black & Veatch
F. Chris Middlebrough – City of Toledo, OH
Carol L. Hufnagel – Tetra Tech
2. 09/14/06 B&V - 2 Background Late 80’s & Early 90’s – Three CSO storage tunnels constructed.
October 1991 – Original US/OEPA vs. Toledo lawsuit.
July 2002 – Toledo voters approve ordinance to settle lawsuit.
Consent decree.
Start of Toledo Waterways Initiative.
3. 09/14/06 B&V - 3 Consent Decree Requirements Discharge from Outfall 002 allowed only when flow exceeds 400 MGD
Activated sludge treatment of all flows up to 195 MGD
60 MG EQ basin (reduced to 25 MG pending EPA approval); dewatered flows must receive activated sludge treatment
185 MGD high rate clarification facilities; may discharge only when flow exceeds 195 MGD & EQ basin is full
Prohibited return of wet weather treatment solids to main plant headworks
4. 09/14/06 B&V - 4 Bay View WWTP Flows Toledo, OH sewer system is 30% combined
Bay View WWTP flows:
45 MGD dry weather
70 MGD average annual
130 MGD peak month
400 MGD peak hour
Maximum flow through secondary treatment is approximately 195 MGD
5. 09/14/06 B&V - 5 HRT Milestones February 2003 - Pilot Test Completed
HRT - DensaDeg® vs. Actiflo ®
UV Disinfection - Medium Pressure vs. LPHO
2005 – Construction Started
October 2006 – Performance Testing of HRT
2007 – Begin Two-Year Effectiveness Study
6. 09/14/06 B&V - 6 HRT Evaluation Factors Discharge Requirements
Frequency of Use/Chemical Usage
Pretreatment Needs
Pumping
Fine Screening
Grit Removal
Odor Control
Startup & Shutdown Requirements
Solids Handling Requirements
Flexibility to Use for Primary & Tertiary Treatment
7. 09/14/06 B&V - 7 HRT Pilot Test Actiflo ® - Kruger (Veolia Water)
DensaDeg® - IDI
8. 09/14/06 B&V - 8 Actiflo DesignConsiderations Fine Screening (< 1/4 inch openings)
f (Hydrocyclone opening)
Requires Grit Removal
Thin Sludge (<0.5% solids);
Volume ~ 2 to 3% of Influent Flow
(= capacity of recirculation
pumps)
Media Recirculation &
Cleaning System
9. 09/14/06 B&V - 9 DensaDeg Design Considerations Fine Screening (< 1/2 inch openings)
Concentrated Sludge (3 to 4% solids)
Slower Startup Due to Reliance on Sludge Recirculation
Potentially deeper settling compartment than Actiflo
Less Consistent Performance Due to Ballast Media (Sludge) Variability
10. 09/14/06 B&V - 10 HRT Intermittent Operation Issues Dry process startup; time required to establish process equilibrium
Handling off-spec effluent
Bringing parallel units on-line
Maintaining a standby operational mode –
necessary for Actiflo
Dewatering to prevent nuisance conditions
11. 09/14/06 B&V - 11 Other Uses for HRT Primary Treatment
Derate to about 1/3 to ½ of Wet Weather Treatment Capacity
Uses less Ferric Chloride than for Wet Weather Treatment
Densadeg better than Actiflo due to solids thickening feature
Dry Weather Tertiary Treatment
Lowers TSS & phosphorus concentrations
Improves chances of meeting 7-day limits when averaged with wet days
12. 09/14/06 B&V - 12 HRT Costs Capital costs very close to the same in most cases
Smaller footprint for Actiflo due to higher loading rates
Less pretreatment required for DensaDeg
If solids cannot be returned to plant influent, solids handling costs are lower for DensaDeg
O&M costs slightly less for DensaDeg due mostly to lower pretreatment requirements
13. 09/14/06 B&V - 13 Reasons for Selection of DensaDeg No additional sludge processing facilities required
No additional fine screening facilities required, increasing amount of screening equipment to be maintained and screenings to be handled
Rapid startup is not an issue
Equipment is the same as existing equipment to service and maintain
No need to maintain a “standby” mode
No microsand and related maintenance and housekeeping issues
14. 09/14/06 B&V - 14
15. 09/14/06 B&V - 15 Bay View WWTP Layout
16. 09/14/06 B&V - 16 Toledo, OhioBay View Wastewater Treatment Plant
17. 09/14/06 B&V - 17 Toledo, OH DensaDeg® Layout
18. 09/14/06 B&V - 18 Toledo, OH DensaDeg® HRT
19. 09/14/06 B&V - 19 HRT Pipe Gallery & Sludge Pumps
20. 09/14/06 B&V - 20 HRT and EQ Basin
21. 09/14/06 B&V - 21 HRT Treatment Results Those were just a couple of graphs from the various performance runs. This table provides a summary of all the various runs.
Normal = 27 mgd x 6 = 162 mgd total
Peak Flow 1 = 185 mgd / 6 = 31 mgd (all units in service)
Peak Flow 2 = 185 mgd / 5 = 37 mgd (firm peak flow)
Average flow performance criteria = >50% TSS removal
Peak flow performance criteria = >70% TSS removal except when TSS<40mg/L and >70% suspended CBOD removal
Influent TSS ranged from 50 to 400 mg/L during week of testing.
40 mg/L ferric chloride & 2 to 3 mg/L polymer.Those were just a couple of graphs from the various performance runs. This table provides a summary of all the various runs.
Normal = 27 mgd x 6 = 162 mgd total
Peak Flow 1 = 185 mgd / 6 = 31 mgd (all units in service)
Peak Flow 2 = 185 mgd / 5 = 37 mgd (firm peak flow)
Average flow performance criteria = >50% TSS removal
Peak flow performance criteria = >70% TSS removal except when TSS<40mg/L and >70% suspended CBOD removal
Influent TSS ranged from 50 to 400 mg/L during week of testing.
40 mg/L ferric chloride & 2 to 3 mg/L polymer.
22. 09/14/06 B&V - 22 First 6 Months of 2-year Effectiveness Study
23. 09/14/06 B&V - 23 Wet Weather Treatment System Performance
24. 09/14/06 B&V - 24 Two-Year Effectiveness Study Ongoing.
Performance testing results verified.
Continuing optimization.
Have met final effluent limitations at flows up to 390 MGD. Including the big rain events of late August 2007.
25. 09/14/06 B&V - 25 Facility Optimization Pilot study and performance testing used 40 mg/L or more FeCl3 and up to 3 mg/L of polymer…
…while City now generally doses 10-30 mg/L FeCl3and 0.5-2 mg/L of polymer.
A lot of DensaDeg® effluent sent to activated sludge system.
Jar testing of recent events to further optimize FeCl3 to polymer ratios.
Generally constant ratio whether dosing 45 and 1.5 mg/L or 15 and 0.5 mg/L (FeCl3 and polymer, respectively).
26. 09/14/06 B&V - 26 Some Lessons Learned Density meters and blanket sludge depth detectors not necessary for intermittent operation
Startup for intermittently operating facility – takes longer to work out glitches – longer warranty period is helpful
Returning HRT effluent to secondary can inhibit nitrification
Alkalinity consumption (HRT + nitrification) ? loss of effluent buffering capacity (pH concerns)
27. 09/14/06 B&V - 27 HRT Construction Costs
28. 09/14/06 B&V - 28 HRT Annual O&M Costs
29. 09/14/06 B&V - 29 Questions ???