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WEF SDC 2011 Expansion of Acton WWTP University of Guelph Team: Alexandra Chan Adam Erb Cynthia Mason Julia Veerman October 16, 2011
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Outline Introduction Population Analysis Process Selection Phase 1 Design Modeling Noise & Odour Control Construction Phase 2 Design Economic Evaluation Conclusions and Recommendations
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Review of Existing Facility
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Problem Statement Current WWTP operating near peak capacity Need to increase capacity to accommodate projected growth in two phases Meet projected effluent criteria
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ParameterCurrent (m 3 /day) Phase 1 Given (m 3 /day) Phase 2 Given (m 3 /day) Average Daily Flow (dry weather)461056007000 Maximum Daily Flow (dry weather) 6160969014307 Instantaneous Peak Flow (wet weather) 159801495521452 Design Basis ParameterExisting Effluent Objective/Limit Proposed Effluent Objective/Limit BOD 5 (mg/L)2/5 TSS (mg/L)3/5 Total Phosphorus (mg/L)0.2/0.30.1/0.2 (Ammonia + Ammonium) Nitrogen (mg/L) Non-freezing period (May 1 to Nov 31) Freezing period (Dec 1 to April 30) 1.0/2.0 1.0/4.0 1.0/2.0 1.0/4.0 Unionized Ammonia (monthly average) (mg/L) Unionized Ammonia (any single sample) (mg/L) - -/0.1 -/0.016 -/0.08 Escherichia Coli (monthly geometric mean density) (#of organisms/100mL) 100/150
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Predicted linear growth Assumed water saving devices at 10% Infiltration/Inflow at 204 L/c/d Population Analysis ParameterCurrentPhase 1 Given Phase 1 Calculated Phase 2 Given Phase 2 Calculated ADF46105600762870008574 MDF61609690101931430711456 Peak1598014955264422145229721
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Process Selection Constraints Accommodate design flows Meet effluent discharge limits Use available land Be compatible with existing facility Criteria Cost effectiveness Integration with existing facility Environmental impact and footprint minimization
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Phase 1 Design
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Process Flow
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Primary Clarifier
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Add two rectangular clarifiers New volume 256 m 3 ADF SOR of 27.5 m 3 /m 2 /day Maximum day flow 62.5% TSS removal 40.3% BOD removal Chain & scraper sludge collector and scum removal system Primary Clarifier
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Secondary Treatment
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Two conventional plug flow activated ‐ sludge system with nitrification Accommodate 1275 m 3 /d required Target MLSS = 4000 mg/L SRT = 12 days Fine bubble aeration Positive displacement blower Designed for max day flow + additional feedback flow Aeration System
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Two additional secondary clarifiers Limiting solid flux concept MLSS = 6620 mg/L Overflow = 31 m 3 /m 2 d Chain & scraper sludge collector and scum removal system Max day flow design Secondary Clarifier
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Tertiary Treatment
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85 mg/L liquid alum with 45% purity – 824 kg/d Addition point in activated sludge tank Chemical Addition
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Dual media deep bed filtration Existing filters work well to meet limits Widely accepted in WWT Easily retrofit Leopold™ Type S™ Underdrain Air scour + surface wash backwash Max day flow design with one filter out of commission SLR of 7.2 m 3 /m 2 /h Filtration http://www.wateronline.com/product.mvc/Universal-Type-S-Underdrain-0002
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UV selected as best disinfection method Trojan UV3000Plus™ system LP/HI lamp Automatic and continuous dose pacing Automated mechanical/chemical cleaning Automatic level controller Sized for peak flow UV Disinfection
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Solids Handling
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Sequential dual-stage digester series Add new series in parallel Methane gas collected for heating Thermophillic Stage 1 SRT 2 days Recirculation pump mixing Mesophillic Stage 2 SRT 8 days Bio-Solids Digester
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Belt press drying after digester Polymer addition Increases solids concentration from ~3% to ~25% Cost-effective in disposal Reduces footprint Sludge Drying
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Mass Balance
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System Controls and Instrumentation Control strategy Increased control and monitoring Small relative capital cost Significant efficiency improvements Biological treatment Aeration accounts for up to 50% energy consumption Matched oxygen demand profile Intelligent feedback control for aeration, RAS, WAS
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Clarifiers Monitoring Sludge pumping control mechanisms Digesters Control for feeding rates, recirculation, heating, withdrawal Tertiary Treatment Flow splitting SCADA Interfacing with SCADA for remote monitoring System Controls and Instrumentation
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Hydraulic Profile
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Projected peak influent concentrations and flows Proposed plant sizing Clarifier modeling based on Lessard and Beck dynamic model Activated sludge modeling completed using the IAWQ1 model Phase 1 – Model Inputs
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BOD and NH3 water quality requirements met Model Shortcomings: Chemical phosphorous treatment or tertiary filtration not accounted for Phase 1 – Model Results
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Currently no odour or noise issues Reduce odour and noise Buffer zone Housing potential equipment Odour and Noise Control
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Completion in 24 months Best management practices: Construct in phases Protect waterways Provide training Conduct inspections Construction
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Phase 2 Conceptual Design
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Modify Plant B aeration basin configuration to plug flow + BNR Investigate: Membrane technology Phosphorus extraction Phase 2 Conceptual Design
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Total Capital Cost Estimate = $24M Phase 1 – Capital Cost
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Annual O&M Cost Estimate = $1.2M Phase 1 – O&M Cost
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Total Capital Cost Estimate = $12M Phase 2 – Capital Cost
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Expansion design to increase the Acton WWTP capacity Preliminary Phase 1 design Additional clarifier, disinfection, and anaerobic digestion trains CAS + nitrification Deep bed dual media filter Belt press Conceptual Phase 2 design Conclusions
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Implement sewer system improvement plan Conduct more simulations Obtain more cost-specific information from manufacturers Conduct pilot tests Recommendations
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Dr. Hongde Zhou, P.Eng., University of Guelph – Faculty Advisor David Arsenault, P.Eng., CH2M Hill – Consulting Advisor Rafiq Qutub, P.Eng., WEAO – SDC Sub- Committee Chair Lauren Zuravnsky, P.E., WEF – Design Competition Sub-Committee Chair Acknowledgements
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