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The Kappe Lecture Stevens Institute of Technology September 21, 2013 George Tchobanoglous Department of Civil and Environmental Engineering University of California, Davis. WASTEWATER TREATMENT TRENDS IN THE 21ST CENTURY. Topics. Part-1 Some Global Trends
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The Kappe Lecture Stevens Institute of Technology September 21, 2013 George Tchobanoglous Department of Civil and Environmental Engineering University of California, Davis WASTEWATER TREATMENT TRENDS IN THE 21ST CENTURY
Topics Part-1 Some Global Trends Part-2 Uncontrollable Events and Unintended Consequences Part-3 Future Trends, Challenges, and Opportunities
Part-1 Some Global Trends that will Impact Wastewater Treatment • Population Demographics Impact of urban spread Urbanization along coastal areas • Climate Change (wetter/dryer) Sea level rise Changing weather patterns • Aging infrastructure
Impact of Coastal Population Demographicson Reuse, Hyperion WWTP, Los Angeles, CA
Urbanization Along Coastal Areas • By 2030, 60-70 percent of world’s population will live near a coastal region • Withdrawing water from inland areas, transporting it to urban population centers, treating it, using it once, and discharging it to the coastal waters is unsustainable.
Impact of Sea Level Rise onWastewater Management Infrastructure
Aging Infrastructure Challenges • Aging wastewater infrastructure (typical age 75 years) in large cities over 100 years old with excessive exfiltration • Flowrateswill continue to decrease resulting in: • Increased corrosion • Most conventional gravity sewer design equations no longer suitable • Increased mass concentration loading factors have impacted wastewater treatment facilities
Part-2 Impact of Uncontrolled Events and Unintended Consequences • Uncontrollable events Natural disasters (e.g., storm surges) Impact of climate change on rainfall intensity Power and chemical costs • Unintended consequences Treatment plant siting (considered previously) Water conservation Treatment plant design/energy usage Excess treatment capacity (e.g., tankage)
Impact of Storm Surges onWastewater Management Infrastructure
Impact of Climate Change on Rainfall Intensity and Operation of WWTP
Unintended Consequence of Sea LevelRise on StormwaterCollectionSystem Courtesy City of San Francisco
Unintended Consequence of Sea Level Rise onStormwater Collection System Courtesy City of San Francisco
Impact of Decreasing Flowrates on Operation of Collection Systems and WWTPs
Impact of Water Conservation and Drought:Solids Deposition, H2S Formation, and Downstream Corrosion due to Reduced Flows
At $0.03/kWh energy efficiency was not an Issue. • Older Treat. Plant Design - Little Concern for: • The use of resources, • The consumption of energy, • Long-term sustainability, and • The carbon footprint
Energy Usage in BiologicalTreatment (e.g., activated Sludge)
Part-3 Future Trends, Challenges,and Opportunities • Paradigm shift in view of wastewater • Alternative collection systems • Energy recovery from wastewater • Enhanced preliminary and pretreatment • Urine separation • Direct and indirect potable reuse • Integrated wastewater management
New View of Wastewater: A Paradigm Shift for the 21st Century WASTEWATER is a RENEWABLESOURCE of ENERGY (heat and chemical), RESOURCES, POTABLE WATER
Alternative Collection Systems for Source Separated Resource Streams
ENERGY RECOVERY FROM WASTEWATER
Energy Content of Wastewater Heat energy Specific heat of water = 4.1816 J/g •°C at 20°C Chemical oxygen demand(COD) C7.9H13O3.7NS0.04 C7.9H13NO3.7 + 8.55O2→ 7.9CO2 + NH3+ 5H2O Chemical energy (Channiwala,1992) HHV (MJ/kg) = 34.91 C + 117.83 H - 10.34 O - 1.51 N + 10.05 S - 2.11A
Required and Available Energy for Wastewater Treatment, Exclusive of Heat Energy • Energy required for secondary wastewater treatment • 1,200 to 2,400 MJ/1000 m3 • Energy available in wastewater for treatment (assume COD = 500 g/m3) • Q = [500 kg COD/1000 m3) (1000 m3) (13 MJ/ kg COD) • =6,000 MJ/1000 m3 • Energy available in wastewater is 2 to 4 times the amount required for treatment
Heat Recovery from Wastewater SOURCE : City of Vancouver, Sustainability website retrieved from http://vancouver.ca/sustainability/neuTechnology.htm FALSE CREEK ENERGY CENTER
ENHANCED PRELIMINARY TREATMENT Grit and Grease Removal
Settling Characteristics of Gritin Wastewater Collection Systems
ENHANCED PRETREATMENT
Alternative Technologies for Primary Treatment and Energy Recovery
ALTERNATIVE TREATMENT TECHNOLOGIES
Alternative Treatment Process Flow Diagrams Based on Primary Effluent Filtration
New Biological Treatment Processes Ambient Temperature Anammox Process
Alternative Wastewater TreatmentWithout Biological Treatment Energyand product recovery Solids processing
RETURN FLOW TREATMENT, FLOW AND LOAD EQUALIZATION, AND RESOURCE RECOVERY
Return FlowsTreatment, Flow Equalization, or Offsite Processing
Phosphorus Recovery as Struvite(magnesium ammonium phosphate hexahydrate)
URINE SEPARATION
Nutrients and Trace Organics in Domestic Wastewater: A Case for Urine Separation Source: Jönsson et al.(2000) Recycling Source Separated Human Urine.
Potential Impacts of Urine Separation On Biological Wastewater Treatment
Nutrient Separation, Storage, and RecoveryFrom Individual Residence
DIRECT AND INDIRECT POTABLE REUSE
Recycling Through Direct and Indirect Potable Reuse
Indirect and Direct Potable Reuse OCWD Windhoek, Namibia ~30% San Diego, CA (Proposed), Singapore, Australia
Typical Flow Diagram for the Production of Purified Water Adapted from OCWD
Microfiltration, Cartridge Filters, Reverse Osmosis, and Advanced Treatment (UV), OCWD