Primary Clarifier Odor Control Replacing Nitrates with D.O. Kevin Jacobs, P.E. ECO Oxygen Technologies

Similar documents
R. E. Speece Vanderbilt University David Clidence President of ECO2

USE OF CHEMICALS TO CONTROL ODORS AND CORROSION IN WASTEWATER SYSTEMS

1/11/2016. Types and Characteristics of Microorganisms. Topic VI: Biological Treatment Processes. Learning Objectives:

Is Oxygen Injection the Solution for Your Collection System Odors and Corrosion?

Presented by. John W. DiTuro. Aqua Dynamic Solutions LLC

ISAM SBR with Blower Assisted Jet Aeration Design Calculations For Lyons, CO WWTP Upgrade

Biological Phosphorus Removal Technology. Presented by: Eugene Laschinger, P.E.

Haluk Bafrali Anue Water Technologies November 19, 2015

CORPORATION THE EXPERIENCED LEADER IN SEQUENCING BATCH REACTOR TECHNOLOGY

HYDROGEN SULFIDE INDUCED CONCRETE CORROSION

Corrosion and Odor Control in Wastewater Systems

CORPORATION THE EXPERIENCED LEADER IN SEQUENCING BATCH REACTOR TECHNOLOGY

Contents General Information Abbreviations and Acronyms Chapter 1 Wastewater Treatment and the Development of Activated Sludge

COMPARISON OF SBR AND CONTINUOUS FLOW ACTIVATED SLUDGE FOR NUTRIENT REMOVAL

Meeting SB1 Requirements and TP Removal Fundamentals

ISAM INTEGRATED SURGE ANOXIC MIX

ATTACHMENT 1 GENERAL FACILITY INFORMATION. BOD5 mg/l mg/l TSS mg/l mg/l NH3-N mg/l mg/l

Odor Dispersion Modeling, Priority Odor Sources, and Recommended Improvements. May 25, 2012

Anaerobic Digester Optimization with Bio-Organic Catalyst. NYWEA 81 st Annual Meeting February 3, 2009 One Year Study November 07 - November 08

ANAEROBIC SLUDGE DIGESTION PROCESS. Prepared By Michigan Department of Environmental Quality Operator Training and Certification Unit

WASTEWATER TREATMENT PLANT MASTER PLAN 6. BUSINESS CASE EVALUATION OF ALTERNATIVES

HIGH RATE TREATMENT AS PART OF THE SOLUTION FOR WET WEATHER FLOWS JUNE

Aeration Basics the Bug s Eye View

RESULTS OF ECOSYSTEMS PLUS INJECTION IN SECONDARY AERATION LAGOONS

Module 20: Trickling Filters Answer Key

NEW BIOLOGICAL PHOSPHORUS REMOVAL CONCEPT SUCCESSFULLY APPLIED IN A T-DITCH PROCESS WASTEWATER TREATMENT PLANT

Environmental Engineering I Jagadish Torlapati, PhD Fall 2017 MODULE 3 WASTEWATER TREATMENT CONTROL PARAMETERS QS = VX F M

New Phosphorus Removal Requirement Tips the Scales: Lessons Learned on Biosolids Management and Odor Control at the Southington CT Treatment Plant.

Anaerobic Digester Optimization with Bio-Organic Catalyst

Activated Sludge Base Notes: for student. Activated Sludge Intro. What is Activated Sludge? 3/12/2012

Biological Wastewater Treatment Processes II: MBBR Processes

Case Study. Biological Help for the Human Race. BiOWiSH Aqua Improves Nutrient Removal in a Wastewater Treatment Plant - Oberon, Australia

RE ENGINEERING O&M PRACTICES TO GET NITROGEN & PHOSPHORUS REMOVAL WITHOUT FACILITY UPGRADES

ECO-ANT21 Process ECO-ANT21 Corporation

Proprietary AquaTron technology incorporates three (3) innovative features that increase its efficiency and reduces cost:

Energy Savings Through Denitrification

UNOX Wastewater System Evaluation, March 10-13, 2008 Draft for Client Review

MBBR Wastewater Treatment Processes

ENHANCING THE PERFORMANCE OF OXIDATION DITCHES. Larry W. Moore, Ph.D., P.E., DEE Professor of Environmental Engineering The University of Memphis

SBR FOR LOW FLOW APPLICATIONS

Troubleshooting Activated Sludge Processes. PNCWA - Southeast Idaho Operators Section Pocatello, ID February 11, 2016 Jim Goodley, P.E.

Phosphorus Removal Treatment Alternatives

Making Your Plant Denitrify

Liquid Phase Collection System Odor Control 101

The Use of Magnesium Hydroxide Slurry as a Safe and Cost Effective Solution for H 2 S Odor, Corrosion, and FOG in Sanitary Sewer Systems

Technologies for Sustainable Wastewater Treatment. Nitrogen Removal from Sludge Dewatering Liquor

A Comparison of Technologies for Hydrogen Sulfide Control from a Lengthy Force Main

BIOLOGICAL PHOSPHORUS REMOVAL PLUS CHEMICAL POLISHING FOR LOW LEVEL COMPLIANCE

SIMPLE and FLEXIBLE ENERGY SAVINGS And PERFORMANCE ENHANCEMENT for OXIDATION DITCH UPGRADES

Aerator for Sewer Odor and Corrosion Control

Winery FAST & Floating FAST

Aerator for Sewer Odor and Corrosion Control

City of Elk River Wastewater Treatment Facility Improvements. Achieving Wastewater Treatment Goals

Determination of Treatment Requirements for Municipal and Private Sewage Treatment Works Discharging to Surface Waters

Removal of High Ammonia Levels from Municipal Wastewater Using Humic Acid and Selective Bio-Augmentation

A Critical New Look at Nutrient Removal Processes

NITROGEN REMOVAL USING SATURATED UPFLOW WOODY FIBER MEDIA. Larry D. Stephens, P.E. 1


American Water College 2010

WWETCO FlexFilter and Bio-FlexFilter

Module 1: Introduction to Wastewater Treatment Answer Key

Center Sanitation District

How to Participate Today

Compact Waste Water Treatment MBR /MBBR Technology

Wastewater Treatment clarifier

By Jack Wendler/Ripon WWTF

2015 HDR, Inc., all rights reserved.

Aeration Blower Requirements. Tom Jenkins 06/15/2016

SMCSD Headworks, Primary and Secondary Treatment Pre-Design

Basic knowledge of Wastewater

Hollywood Chemical Injection Facility

Ditches for Energy Efficiency and Improved Nitrogen Removal

Case Study. BioMagic. Variable Dosing Yields Economy and Results CITY OF CARLSBAD. Pump station odor and hydrogen sulfide control

Module 17: The Activated Sludge Process - Part III Answer Key

Maximizing Secondary Wet Weather Capacity at the Columbia Boulevard Wastewater Treatment Plant

VILLAGE OF ALGONQUIN 2014 WASTEWATER FACILITY PLAN UPDATE EXECUTIVE SUMMARY

Appendix B-1. Design Calculations for Sewage Treatment Plant

Integrated Activated Sludge and Biosolids Treatment to Conserve Energy & Waste Solids Disposal

Appendix D JWPCP Background and NDN

Effective Use of Carbon in Nutrient Removal Systems

ENHANCED TECHNICAL ASSISTANCE EVALUATION

Bloomingdale WWTF Private/Public Partnership Works. Bob Wilcox, PE Fleis & VandenBrink May 10, 2016

The ABC s (and 123 s) of Treating High Strength Wastewater

Optimization of an Aeration System at an Industrial Wastewater Treatment Plant

Membrane Biofilm Reactor (MBfR): A New Approach to Denitrification in Wastewater Setting

Coupling Trickling Filter or RBC s with Activated Sludge

Wastewater Tools: Activated Sludge and Energy Use Analysis

A Novel Test Method for Measurement of MIC in a Wastewater Collection System. Tim Matheis Evoqua Water Technologies LLC

CEE 371 May 14, 2009 Final Exam

Chapter 2: Description of Treatment Facilities

Assuming 100 gallons per capita per day, and 3 people per REU, design flows for the development are proposed to be:

2015 Spring Conference

AquaPASS. Aqua MixAir System. Phase Separator. System Features and Advantages. Anaerobic. Staged Aeration. Pre-Anoxic.

Turbo4bio System For the Treatment of Sewage & Organic Effluents

Copies: Mark Hildebrand (NCA) ARCADIS Project No.: April 10, Task A 3100

AALSO Summary of Formulas needed for Levels I, II and III.

Aeration System Improvements with a 5-Year Payback. Scott Phipps

AMENA Conference May 12 nd 13 th, 2011 Guadalajara, Mexico

Client: City of Pontiac Project Name: Regional WWTP Feasibility Location: Pontiac, MI Project Number: Issue Date: October 23, 2006

ECO Smart Aerobic Waste Water Treatment System. Optimising the re-use and recycling of waste water

Transcription:

Primary Clarifier Odor Control Replacing Nitrates with D.O. Kevin Jacobs, P.E. ECO Oxygen Technologies

Presentation Outline Primary Clarifier Odor Challenges Odor Treatment Options Case Study Anson-Madison Sanitary District Conclusions

Primary Clarifier Odor Challenges

Quiescent by Design Flow is slowed to allow for solids settling Provides for little to no re-aeration

Major Odor Source The effluent weirs from a primary clarifier are a major source of odor Odor Release H2S Flux H2S Flux Sludge Blanket

Root Cause of Odor Electron Acceptors (Order of Preference): Oxygen Nitrate Sulfate U.S. EPA (1985) Odor and Corrosion Control in Sanitary Sewerage Systems and Treatment Plants Design Manual; EPA/625/1-85/018; Cincinnati, Ohio.

Root Cause of Odor Under Anaerobic Conditions: Bacteria consumes BOD Strips Sulfate of O2 Converts Sulfate to Sulfide SO4 & BOD H2S Sulfide No D.O.

Factors That Affect H 2 S Formation Limited solubility of oxygen in water High BOD Favorable ph levels Warm temperatures Unlimited supply of sulfates Long retention times

Odor Leads to Corrosion 100% Rate of Corrosion 50% 0 5 500 H2S Concentration (ppm) 1000

Corrosion

Common Solutions Allow H 2 S to Form and Treat Cover and Scrub Wet scrubbers Carbon units Biofilters Biotrickling Filters Chemical Addition Nitrate Iron Prevent H 2 S Formation Oxygen addition

Form and Treat Solutions

Form and Treat Solutions

Chemical Addition

Preventive Solution D.O. Addition No bubbles = No impact on settling Add enough D.O. to satisfy HRT Consume BOD ahead of aeration H2S Flux Aerobic Cap Sludge Blanket H2S Flux

SuperOxygenation as a Preventive Solution 40 mg/l at 1 ATM - Increasing pressure increases the saturation point - Use of pure oxygen versus air

SuperOxygenation Technology Overview Side Stream Pump ECO 2 Cone 90-95% O2 Absorption Efficiency Pure Oxygen Gas Unscreened Raw Wastewater Conveyance Pipeline SuperOxygenated Raw Water

Case Study Anson Madison Sanitary District Madison, ME Operated by Woodward and Curran 4 MGD Flow 3.5 MGD from UPM- Madison Paper 0.5 MGD from local community

Case Study Anson Madison Sanitary District Madison, ME Plant is located in close proximity to neighbors Frequent odor complaints

Case Study Anson Madison Sanitary District Madison, ME Physical Characteristics Diameter 90 ft Depth 12 ft Volume 0.57 MG Normal HRT 3.5 5 hours

Case Study Anson Madison Sanitary District Madison, ME Wastewater Characteristics Temperature 28-30 BOD 500-600 mg/l Oxygen Uptake Rate (OUR) 5-10 mg/l/hr PC Flow (MGD) HRT (hrs) OUR (mg/l/hr) 3.9 3.1 5.36 1.9 6.3 10.47 2.6 4.6 8.86 2.8 4.3 5.65

Primary Clarifier Odor No Treatment

Use of Nitrates Original Design 200 gpd = ~750 lbs O 2 @ $2.50/gal = $183,000 not working! Actual required dosage 400 gpd = 1,500 lbs O 2 @ 2.50/gal = $325,000

Design Calculations Low Flow Scenario: 2.7 MGD Flow results in 5 hour HRT 5 hr * 10 mg/l/hr * 8.34 * 2.7 MGD = 1,125 lbs O 2 /day Average Flow Scenario: 4 MGD Flow results in 3.5 hour HRT 3.5 hr * 10 mg/l/hr * 8.34 * 4 MGD = 1,168 lbs O 2 /day Peak Flow Scenario: 6 MGD Flow results in 2.3 hour HRT 2.3 hr * 10 mg/l/hr * 8.34 * 6 MGD = 1,151 lbs O 2 /day

SuperOxygenation System Design Considerations Available primary influent pump head capacity All influent pumped through cone Pump TDH at 25 Cone located at grade Resulting system capable of adding 1,680 lbs O 2 /day Up to 62 mg/l D.O. achieved

SuperOxygenation System Placement System capitalizes on PC pump head and available static head

Primary Clarifier Pumps

Oxygen Generators (2) 200 lpm (840 lbs/day) units generate oxygen at 93% purity

Economics ECO 2 Nitrates Chemical Cost $325,000 Oxygen Cost 254 kwhr/day per generator at $0.147/kwHr $27,250 Annual Savings $297,750 Equipment Capital Cost ECO 2 System, (2) O 2 Generators Installation Cost Engineering, piping, instrumentation, generator building, etc. Payback $310,000 $270,000 <2 years Oxygen cost reflects full operation of both generators

D.O. at Cone Discharge

H 2 S Level at Weir

D.O. Level at Weir

Measurement Location

Treatment Benefits Achieved H 2 S control is consistent Odor complaints eliminated BOD reduction across clarifier increased Prior to oxygen addition 15% removal Adding 1,000 lbs O 2 /day has increased BOD removal to 20% Additional 600-1,000 lbs BOD/day removed Less oxygen required in aeration $25,000-$40,000 additional annual savings

Revised Economics ECO 2 Nitrates Chemical Cost $325,000 Oxygen Cost 193 kwhr/day per generator at $0.147/kwHr $20,500 Aeration Savings $25,000 Annual Savings $329,500 Equipment Capital Cost ECO 2 System, (2) O 2 Generators Installation Cost Engineering, piping, instrumentation, generator building, etc. Payback $310,000 $270,000 1.76 years

Conclusions Operationally Compatible No impact to settling Efficient 90-95% oxygen absorption efficiency Oxygen is added to meet flow demand Economical Oxygen is inexpensive in comparison to alternatives District saves ~$300,000 per year over nitrates Reduced aeration requirements Effective H2S levels typically near non-detect

Acknowledgements Dale Clark, AMSD Plant Manager, Woodward and Curran

Questions? Kevin Jacobs (317) 706-6487 kjacobs@eco2tech.com