PD-Sw205w 1 1 FOSNRS 2: Passive, 2-Stage Biofilter Treatment Systems for Reduction of Nitrogen from OWS – Pilot Study Results April 7, 2014 Josefin Hirst,

Slides:



Advertisements
Similar presentations
1000 Friends of Florida Presentation on May 12, 2005 Presenter: Kart Vaith/CDM
Advertisements

Alternatives to Aboveground Effluent Disposal Mounds Overview of the NoMound ® System Technology.
Deep Bed Denitrification Performance
Anne Arundel County Department of Public Works
Biological waste water treatment
Wastewater treatment steps Primary: solids removal (physical) Secondary: BOD treatment (biological) Tertiary: Effluent polishing, Nutrient and Toxins Removal.
Constructed Wetlands pp CIDWT Disclaimer These materials are the collective effort of individuals from academic, regulatory, and private sectors.
WATER DEPTH, VEGETATION, AND POLLUTANT REMOVAL IN A CONSTRUCTED WETLAND TREATING AQUACULTURE EFFLUENT Brian E. Dyson, Kim D. Jones, Ron Rosati* Department.
Herwig Goldemund, Ph.D. Geosyntec Consultants Atlanta Regional Office
Nutrient Removal and Power Savings in Wastewater Treatment Systems
Advanced Pretreatment: Proprietary Configurations, Operational Issues and O&M.
Leachate Treatment at Virginia Landfills By: Bob Gardner, PE, BCEE Senior Vice President SWANA Old Dominion Conference Wintergreen, VA August 7, 2014.
Trickling Filters and Rotary Biological Contactors
Phosphorus Removal at Sand Creek Water Reuse Facility by Duane “Bear” Steib and Kathy Bill/City of Aurora Steve Polson/CH2M HILL by Duane “Bear” Steib.
Septic Tank x Drain Field Biological and Chemical Functions BOD 5 = the biological oxygen demand, i.e., the quantity of oxygen consumed by microorganisms.
Tertiary Treatment: Nutrient Removal, Solids Removal, and Disinfection.
Nitrogen Removal from Yamuna River (India) using MBBR – Pilot Summary
Nitrification and Denitrification
What is Nitrogen?  Nitrogen makes up about 78% of our atmosphere.  Nitrogen in the atmosphere it is mostly in the form of ______, which is a compound.
Moving Bed Biofilm Reactor MBBR for Nitrification/Denitrification
The Nitrogen Cycle.
ROTATING BIOLOGICAL CONTACTOR (RBC) PROCESS
Attached Growth Biological WW treatment Systems
WASTE WATER TREATMENT FOR RITONAVIR PRODUCTION PLANT Presented by Wang Dong Mei July 8, 2000.
7.1 Wastewater Treatment Process
Nitrification Frequently Asked Questions NitrobacterNitrosomonas Note: There are other bacteria capable of nitrification. These are the only ones that.
I-70 Greenfield Rest Area Constructed Wetland Wastewater Treatment System Research Project (SPR-2455, SPR-2456, SPR-2487) R. S. Govindaraju, J. E. Alleman,
OutlineBackground Conventional on-site systems Advanced treatment systems.
Effective Use Of Peracetic Acid to Reduce Effluent Disinfection Byproduct in Water Resource Recovery Facilities Isaiah Shapiro, EIT Dimitri Katehis PhD,
The nitrogen cycle is the biogeochemical cycle that describes the transformations of nitrogen and nitrogen- containing compounds in nature biogeochemical.
Overview of Systems Engineering
© 2004 Wadsworth – Thomson Learning Chapter 28 Microorganisms and the Environment.
What is EcoMachine?  It is a machine that reduces water consumption in the Aiken Center by treating sewage exiting the building and then returning it.
Basic Treatment Train Diagrams Keep in mind…variations are ALWAYS possible.
Wastewater Treatment Processes
Adjusting N:P ratios in liquid dairy manure through nitrification and chemical phosphorus removal to match crop fertilizer requirements Background Nutrient.
Sewage Treatment.
Freshwater recirculation systems
Bioremediation Systems to Treat Nursery Runoff Chris Wilson and Tom Yeager University of Florida/IFAS Joe Albano USDA/ARS Horticultural Research Lab.
ENHANCED WASTEWATER TREATMENT FOR UPLANDS FARM COLD SPRINGS NY.
Engineering SND Wastewater Treatment in the Classroom Sarah Sanford 1, Ann Sager 2, Sarina Ergas 2 1. T.R. Robinson; 2. Department of Civil and Environmental.
COMPARISON OF MBBR AND Suspended growth BNR Performance at the HRWTF
Electricity | Natural Gas | Water | Wastewater Adding Whey for Denitrification Dale Adams, P.E Managing Engineer, Colorado Springs Utilities September.
Cody Guenzler, Period 3 Nitrogen Fixation Conversion of Nitrogen Assimilation Ammonification Nitrification Denitrification.
Ammonium removal with the anaerobic ammonium oxidation Song-E Baek.
ZEOLITE ANAMMOX DE-AMMONIFICATION PROCESS Robert Collison PhD PE
Introduction to Recirculating Aquaculture Systems (RAS)
Water Treatment Drinking water : Held in a holding tank settling the suspended matter. Colloidal materials such as clay are removed from water by using.
Membrane Bioreactors for Wastewater Treatment.
WATER MANAGEMENT.
RESEARCH AND DEMONSTRATION CENTER ON-LOT SYSTEMS AND SMALL FLOW TECHNOLOGIES DELAWARE VALLEY COLLEGE DOYLESTOWN, PA Project Funding Provided by: Pennsylvania.
Welcome to the Key Largo Wastewater Treatment Plant.
Bold & Gold ® Nutrient Removal from On-site Wastewater and Stormwater Systems Plastic Tubing Industries, Inc. (PTI) Licensed Distributor of Bold & Gold.
National University Of Kaohsiung Taiwan
Chapter 7 - Fundamentals of Biological Treatment
Attached Growth Biological WW treatment Systems

MARINE (SALT WATER) AQUARIUM 101
Wastewater Treatment Dr.Gulve R.M..
Dissolved Oxygen and Biochemical Oxygen Demand Analyses
DTF TREATMENT PROCESSES
November 4, 2015 Elke Ursin, PMP, CPM
Wastewater Treatment Secondary Treatment.
Nitrogen Cycle.
Authors: Kristen McCarty, Gabrielle Young, Luke Plante
Nitrogen Cycle review.
What is Nitrogen? Nitrogen makes up about 78% of our atmosphere.
Assessment of MBR for Bacteria & Nitrogen Reduction
Nitrogen Removal University of Kansas
Advanced Wastewater Treatment
Presentation transcript:

PD-Sw205w 1 1 FOSNRS 2: Passive, 2-Stage Biofilter Treatment Systems for Reduction of Nitrogen from OWS – Pilot Study Results April 7, 2014 Josefin Hirst, P.E. The Florida Onsite Sewage Nitrogen Reduction Strategies (FOSNRS) Project SSSA Onsite Wastewater Conference April 7-8, 2014 Hazen and Sawyer, P.C.

PD-Sw205w 2 Presentation overview ■FOSNRS Task A: Nitrogen treatment and reduction options for Florida ■Pilot test results ■Summary ■Questions and answers

PD-Sw205w 3 3 FOSNRS Task A: Nitrogen treatment and reduction options for Florida

PD-Sw205w 4 Review of biological nitrogen reduction for onsite wastewater treatment Primary Treatment Mineralization of organic N to ammonia (NH 4) Nitrification Ammonia oxidized to nitrate (NO 3 ) by nitrifying bacteria, requires oxygen Denitrification Nitrate converted to N 2 gas by denitrifying bacteria in anoxic environment; requires supply of electron donor Dispersal Effluent discharge to the soil or landscape for final treatment

PD-Sw205w 5 What are “Passive” nitrogen reduction systems (PNRS)? ■Most current N-reducing onsite systems are mechanical treatment units, with pumps, blowers, controls ■Passive definition for this project: Passive nitrogen reduction systems (PNRS) are OSTDS that reduce effluent N using reactive media for denitrification and a single liquid pump, if necessary. ■Earlier work showed feasibility of bench-scale “passive” two stage biofiltration concepts (Smith et. al., 2008) Treatment Media Effluent TN (mg/L) TN Reduction (%) Zeolite & Sulfur Media2.297 Expanded Clay & Sulfur

PD-Sw205w 6 Task A was designed to further the concepts developed in previous work ■Developed detailed performance data for passive biofiltration designs with various media configurations ■Produced scalable design criteria from pilot scale biofilters for subsequent full-scale testing ■Evaluated single pass and recirculating stage 1 biofilters ■Evaluated twenty-two biofilters consisting of nine unsaturated Stage 1 biofilters, nine saturated Stage 2 biofilters, and four vertically stacked biofilter designs.

PD-Sw205w 7 A unique pilot facility was constructed at UF research center ■University of Florida, Institute for Food & Agricultural Sciences (IFAS) ■475 acres of land in SE Hillsborough County ■Facility conducts agricultural research & trials for vegetables, fruit and ornamental plants ■Experts in soil and water science onsite Source:

PD-Sw205w 8 Test facility included numerous treatment trains ■All used two-stage biofilters: ●Stage 1 Nitrification ●Stage 2 Denitrification ■Stage 1 unsaturated filters included 2 media layers and evaluated 15” and 30” media depths ■We also evaluated single pass and recirculating stage 1 biofilters ■For denitrification, we evaluated both lignocellulosic and sulfur denitrification biofilters

PD-Sw205w 9 Various nitrification media were studied Zeo-Pure clinoptilolite Expanded polystyrene Examples of Stage 1 Media Expanded clay Torpedo sand

PD-Sw205w 10 Various denitrification media were also studied Elemental Sulfur Lignocellulosics Examples of Stage 2 Media Oyster shell (alkalinity amendment)

PD-Sw205w 11 PNRS test facility construction Setting up tanks Mixing Media Batches Gravel Underdrain

PD-Sw205w 12 Placing media in tanks

PD-Sw205w 13 Two stage single pass biofilters Stage 1 HLR 3 gal/d-ft 2 Stage 2 HLR 5.6 gal/d-ft 2

PD-Sw205w 14 We tested five trains of two-stage single pass treatment units

PD-Sw205w 15 Two-stage single pass biofilters Stage 1 Unsaturated Biofilters - Nitrification Stage 2 Saturated Upflow Biofilters - Denitrification

PD-Sw205w 16 Stage 1 recirculating biofilters schematic Nitrified Effluent Holding Tank Stage 1 HLR 3 gal/d-ft 2 Recycle Ratio 3:1 Stage 1

PD-Sw205w 17 Horizontal stage 2 biofilters schematic Peristaltic Pump Sample Ports Nitrified Effluent Stage 2 HLR 10 gal/d-ft 2

PD-Sw205w 18 Four recirculating stage 1 trains were followed by four stage 2 horizontal biofilters

PD-Sw205w 19 Stage 1 recirculating biofilters & Stage 2 horizontal saturated biofilters Stage 2 Saturated Biofilters - Denitrification Stage 1 Unsaturated Biofilters - Nitrification Pump Tank Nitrified Effluent Pump Tank

PD-Sw205w 20 PD-Sw205w 20 Pilot test results

PD-Sw205w 21 PNRS pilot testing influent STE quality cBOD 5 TSSTNTKNNH 3 -N Total Alkalinity Septic tank effluent (STE) n mean std. dev min max

PD-Sw205w 22 Stage 1 nitrification biofilters mean effluent values BiofiltercBOD 5 TSSTNTKNNH 3 -N(NO 3 +NO 2 ) Single Pass XCLAY – 15” XCLAY – 30” CLINO – 15” CLINO – 30” Recirculating SAND – 30” XCLAY – 30” CLINO – 15” CLINO – 30”

PD-Sw205w 23 Stage 1 single pass biofilters nitrogen time series Single Pass Expanded Clay: 30 inch depthSingle Pass Clinoptilolite: 30 inch depth CLINO – 30”XCLAY – 30”

PD-Sw205w 24 Recirculating Expanded Clay: 30 inch depth Stage 1 recirculating biofilters nitrogen time series CLINO – 30”XCLAY – 30” Recirculating Clinoptilolite: 30 inch depth

PD-Sw205w 25 Stage 1 nitrification biofilters effluent nitrogen box and whisker plots XCLAY-15” XCLAY-30” CLINO-15” CLINO-30” XCLAY-30” SAND-30” CLINO-15” CLINO-30” XCLAY-15” XCLAY-30” CLINO-15” CLINO-30” XCLAY-30” SAND-30” CLINO-15” CLINO-30” Single PassRecirculatingSingle Pass Recirculating Ammonia Nitrogen, mg N/L Nitrate & Nitrite Nitrogen, mg N/L

PD-Sw205w 26 Stage 2 denitrification biofilters mean effluent values BiofilterC-BOD 5 TSSTNTKNNH 3 -N(NO 3 +NO 2 ) Upflow SULFUR-30% LIGNO-50% SULFUR-80% LIGNO-25% LIGNO-30% Horizontal SULFUR-80% SULFUR-30% LIGNO-50% GLYCEROL

PD-Sw205w 27 Stage 2 upflow single pass biofilters nitrogen time series SULFUR-80% LIGNO-50%

PD-Sw205w 28 Stage 2 horizontal biofilters nitrogen time series SULFUR-80%LIGNO-50%

PD-Sw205w 29 Stage 2 denitrification biofilters effluent nitrogen box and whisker plots Mean = 14.2 SULFUR-30% LIGNO-50% SULFUR-80% LIGNO-25% LIGNO-30% SULFUR-30% SULFUR-80% LIGNO-50% GLYCEROL SULFUR-30% LIGNO-50% SULFUR-80% LIGNO-25% LIGNO-30% SULFUR-30% SULFUR-80% LIGNO-50% GLYCEROL Upflow Horizontal Upflow Horizontal Nitrate & Nitrite Nitrogen, mg N/L Total Nitrogen, mg N/L

PD-Sw205w 30 Single pass systems total nitrogen removal SULFURLIGNOCELLULOSIC

PD-Sw205w 31 Recirculating systems total nitrogen removal SULFURLIGNOCELLULOSIC

PD-Sw205w 32 Vertical sampler profile in Upflow biofilters lignocellulosic issues

PD-Sw205w 33 Lignocellulosic biofilters hydraulic retention time issues

PD-Sw205w 34 Solute profile in sulfur upflow biofilter sulfate production vs nitrate reduction

PD-Sw205w 35 Single pass vs recirculating biofilters: sulfate

PD-Sw205w 36 Lessons learned from pilot test ■Encouraging results from pilot PNRS; several system configurations capable of > 95% N reduction ■Sulfate production vs nitrate reduction ■Highly reactive elemental sulfur media ■Lignocellulosic retention time issues ■Recommended evaluation of combination lignocellulosic and elemental sulfur denitrification systems for full-scale treatment units

PD-Sw205w 37 PD-Sw205w 37 Questions? Josefin Edeback-Hirst, P.E. Hazen and Sawyer, P.C Princess Palm Avenue, Suite 200 Tampa, FL