Design Considerations for High Strength Wastewater

Slides:



Advertisements
Similar presentations
EO TP3 SAMPLING WASTE DISPOSAL SYSTEMS.
Advertisements

BAT Work Group. BAT Work Group Goals Develop a procedure for identifying technologies eligible for funding Propose policies and regulation necessary to.
Septic Tank, Grease Trap, and Holding Tank Standards and Specifications AOWA:Basic Installer Course1 (1)A new, replacement, or repaired septic.
Sewage and Effluent Treatment 2-4 November 2002 Seán Moran -The first few slides.
ENVE 420 Industrial Pollution Control EQUALIZATION Dr. Aslıhan Kerç.
Treatment of Slaughterhouse Wastewater
Biological waste water treatment
Soneva Gili Resort Comments on existing STP 27. August 2008.
Organic vs. Hydraulic Loadings On-site Treatment Systems J. R. (Jack) Harman, P.E. North Carolina Annual OnSite Wastewater Conference October 18, 2010.
Introduction to Septic Tanks John R. Buchanan, Ph.D., P.E. University of Tennessee.
Introduction to Environmental Engineering Code No. (PE389) Lec. 6.
Wastewater Treatment Plants & Bacteria: Strategies for Compliance Wastewater Collection Systems Teague Harris Pate Engineers, Inc. John Montgomery Municipal.
Harris County Onsite Wastewater Reuse Program John Blount, P.E. Director of Planning & Operations.
HOUSE BILL 89 ONSITE WASTEWATER STAKEHOLDER MEETING 2 nd meeting September 8, 2011 Crystal Lovett, MO DNR Facilitator, and DNR-DHSS Panel.
GREASE INTERCEPTION IN THE PLUMBING CODE Dave CantrellDave Cantrell Public Health – Seattle & King CountyPublic Health – Seattle & King County.
Wastewater Characterization NC Subsurface Operator School.
Basic Installer Course. AOWA:Basic Installer Course Square foot.
On-site Sewage Facility (OSSF) Trends in Texas
1 CE 548 Analysis and Selection of Wastewater Flowrates and Constituent Loading.
WASTEWATER ENGINEERING
1 RATE SETTING WORKSHOP February 23, RATE CHANGES In accordance with Section of the Charter Plan of the District, any proposed rate change.
Flow Equalization Tanks Presented by Keith Surface.
Alabama Dept of Public Health New Onsite Regulations Overview of Permitting Requirements.
Stormwater Systems ARCH-433. Attendance This water closet, installed in Pullman, Washington, flushes in a counterclockwise rotation. In what direction.
CE 3372 Water Systems Design
Deborah Helstrom, P.E. Utilities Technical Review Water Supply Division Membrane Bioreactors Treatment Systems.
3rd Annual Harris County On-site Wastewater Seminar
Rule Change Update MPCA 1/13/ Mid-Sized ISTS (MSTS)
By: John R. Blount, PE, LEED AP Director Harris County Architecture & Engineering Division.
7.1 Wastewater Treatment Process
Kara Denney Industrial Wastewater Permit Writer Water Quality Division.
L.R. Chevalier, Ph.D., P.E., D-WRE, BCEE, F-ASCE Curriculum for Sustainability at Southern Illinois University Carbondale Based on Chevalier, L.R., 2010,
Environmental Health X. Rodents and Insects Shu-Chi Chang, Ph.D., P.E., P.A. Assistant Professor 1 and Division Chief 2 1 Department of Environmental Engineering.
Smart Growth / Smart Energy Toolkit Wastewater and Higher Densities Achieving Higher Density Development In Areas Without Sewer/Water Service Smart Growth.
Wastewater generation
1 IV. Wastewater Treatment technologies Topic IV. 9. Wastewater Treatment Facilities with Suspended Biomass - Aerated Tanks: Kinds, Structures, Basic Technological.
AN ADVANCED URBAN WATER MANAGEMENT CONCEPT: GRAYWATER SEPARATION Sybil Sharvelle September 11, 2008.
Massachusetts Public Health Inspector Training Wastewater Certificate Program (MA PHIT WW) Session 5: Design and Plan Review— Non-Conventional Systems.
Technical Review Needed Fire Flow Analysis Developer Services Summit November 16, 2010 Engineering - Asset Planning Joe Dugandzic, PE.
Implementing Rain Water Harvesting into Building Construction in VA Presented by: Guy Tomberlin, CBO Code Specialist III Fairfax County DPWES, Land Development.
Rules Overview: Why Do We Do What We Do Alisa Max, P.E. Harris County Alisa Max, P.E. Harris County.
Environmental Technology Wastewater Management Module 6.0.
Wastewater Treatment Processes
Integrated Constructed Wetlands Regulatory Aspects - the EPA’s role Aoife Loughnane Inspector, Environmental Licensing Programme Environmental Protection.
Deborah Helstrom, P.E. Industrial Permits Team Wastewater Permitting Section Membrane Bioreactors Treatment.
La. Food Processors Conference Facility Upgrade and Expansion Considerations for Treatment of Process Waste Todd Farrar, P.E.M. General Engineering & Environmental.
1 Large On-site Sewage Systems Maryanne Guichard May 16, 2008.
An Introduction To Modeling of Surface Waters For TPDES Permits Mark A. Rudolph, P.E. TCEQ Water Quality Division.
Introduction to Environmental Engineering Dr. Kagan ERYURUK
Public Information Meeting Wastewater Treatment January 26, 2016.
COMPARISON OF MBBR AND Suspended growth BNR Performance at the HRWTF
18/09/2006 Environmental Protection Agency Improvement of the Statistics on Industrial Water Use and Waste-Water Discharges Lithuania Project presentation.
NH International (Caribbean) Ltd Penal Rock Hindu School Presented by : Sudesh Ramroop.
Administration Code Changes to Incorporate Graywater Policy Principles Jayne Joy, P.E. Director, Environmental & Regulatory Compliance January 2016 EASTERN.
WATER MANAGEMENT.
 Overview: Wastewater Engineering  Wastewater Characteristics  Wastewater Treatment Considerations  Overview: Wastewater Treatment Plant Design.
1 CTC 450 Review WW Sludge Processes. 2 Objectives Understand the basics with respect to operation of wastewater systems.
CTC 450 Review WW Sludge Processes.
Transitioning from the Percolation Test to Soils Evaluation
Department of Environmental Quality
Biosolids Public Workshop March 22, 2016
Wastewater Surcharge Reduction for Manufacturing Processes
Reduction of Accumulated Solids
BRENT LAWSON STATE PLUMBING INSPECTOR SUBSURFACE WASTEWATER
Introduction If nontoxic organic pollutants get discharged into a river, lake or stream, they should be pretty harmless, right?
David Gustafson Emerging Issues David Gustafson
Wastewater Treatment Secondary Treatment.
Wastewater Treatment: Characteristics and Systems
BAT Work Group.
2019 Environmental Trade Fair & Conference Monica Vallin-Baez
Presentation transcript:

Design Considerations for High Strength Wastewater John R. Blount, P.E. Harris County Public Infrastructure Department Assistant County Engineer Director, Architecture & Engineering Division

Topics Define high strength wastewater Discuss hydraulic vs. organic loading Explore results of Harris County high strength wastewater studies Review relevant sections of 30 TAC §285 Develop strategies for moving forward

What is high strength wastewater? Wastewater that has higher amounts of BOD, TSS, or FOG than residential wastewater Residential wastewater Strength < 300 mg/L BOD* High strength wastewater Photos: http://www.clker.com/clipart-scales-of-justice-3.html, http://www.aediconstruction.com/sustainability/low_flow_water_fixtures.html, http://www.bls.gov/ooh/Production/Food-processing-occupations.htm * Per 30 TAC §285.32(f)2

What is high strength wastewater? It is often highly variable For example, a restaurant with a lunch rush http://www.southpaceblog.com/2012/11/06/what-to-expect-in-todays-restaurant-market/

Why should I be concerned? Conventional systems will not work well with high strength wastewater due to clogging of the soil interface. High strength wastewater can cause faster decline of onsite systems without adaptations. Photo: http://bbprof.wordpress.com/2012/03/22/a-d-in-rhetoric/

Quantity vs. Quality Hydraulic loading Organic loading Water volume Organic loading Water quality Know what you’re dealing with- do your detective work! Photo: http://www.glogster.com/1jbfan/detective-work/g-6n94f14apu919am1ppmuhdh

How strong is strong? Total Daily Load Wastewater Flow Rates (gal per hour) + Wastewater quality Overall wastewater strength Agnoli, T. 2000. The best wastewater systems consider flow rate and waste strength. Small Flows Quarterly, 1 (2).

Texas Restaurant Wastewater Analysis, 2003 Pretreatment is necessary to prevent system failure Highlighted the need for a design manual for restaurants Parameter Typical domestic waste (range, mg/L) Restaurant waste (average, mg/L) BOD 100-400 1,202 COD 100-300 1,717 TSS 100-350 318 FOG 16-65 131 Study funded by the Texas Onsite Wastewater Research Council

Not all restaurants are created equal Restaurant type BOD mg/L, avg TSS mg/L, avg FOG mg/L, avg 6 Fast food 2,137 233 102 1 Pizza 1,856 321 183 4 Chinese 1,364 448 241 9 Mexican 1,254 668 190 American 1,063 297 147 American Buffet 792 195 63 2 Steakhouse 601 160 77 3 Seafood 555 229 47 Typical residential waste 100-400 100-350 16-65

Texas Restaurant Wastewater Analysis, 2003 BOD mg/L COD mg/L TSS mg/L FOG mg/L BOD lbs/day Hand wash 5 2,617 2,575 366 120 30.5 Commercial Dishwasher 22 1,037 1,912 418 153 36.9 Values shown are averages

Texas Restaurant Wastewater Analysis, 2003 BOD mg/L BOD lbs/day Conventional fixtures 973 22 Low flow fixtures 1,309 36

Harris County Low Flow Fixture Study, 2013 Initiated November 2013 Compare BOD, TSS, and FOG from an older residential neighborhood to a new neighborhood with low flow fixtures (and therefore, high strength wastewater) http://stockfresh.com/image/1722713/pending-rubber-stamp

What about NSF 40? However… Example: Fast food restaurant with 33 seats, loading factor of 15 gpd/seat According to TAC, 15 x 33 = 495. It might be assumed a 500 gpd treatment plant would suffice. However…

What about NSF 40? NSF Standard 40 treatment plants assume BOD= 240 mg/L Harris County restaurant study average BOD = 1202 mg/L: 5 times greater! Reality is this scenario would require a 2,500 gpd plant if you look at it on an organic loading basis.

What does the TAC say? “(1) Tank sizing. Proprietary treatment systems that serve single family residences, combined flows from single family residences, or multi-unit residential developments shall be designed using Table II in §285.91(2) of this title unless there is an equalization tank preceding the aerobic treatment unit. If there is an equalization tank preceding the aerobic treatment unit, the equalization tank shall meet the requirements set forth in §285.34(b)(4) of this title (relating to Other Requirements) and the aerobic treatment units can be sized using the wastewater flows in Table III in §285.91(3) of this title.” 30 TAC §285.32(c)

Table III- Wastewater Usage Rate Table III ONLY applies to hydraulic loading “This table shall be used for estimating the hydraulic loading rates only. Sizing formulas are based on residential strength BOD5. Commercial/institutional facilities must pretreat their wastewater to 140 BOD5 prior to disposal unless secondary treatment quality is required. For design purposes, restaurant wastewater will be assumed to have a BOD5 of at least 1,200 mg/l after exiting the grease trap or grease interceptor.” 30 TAC §285.91(3)

What does the TAC say? “Proprietary units under this section have been approved to treat flows equal to or less than their rated capacity and with an influent wastewater strength ranging from a 30 day average Carbonaceous Biological Oxygen Demand (CBOD) concentration between 100 milligrams per liter (mg/l) and 300 (mg/l) and a 30 day average TSS concentration between 100 mg/l and 350 mg/l.” 30 TAC §285.32(c)5(A)i

What does the TAC say? “Restaurant/food establishment sewage. When designing for restaurants, food service establishments or similar activities, the minimum design strength value shall be 1,200 mg/L Biochemical Oxygen Demand (BOD) after a properly sized grease trap/interceptor. It is the responsibility of the designer to properly design a system which reduces the wastewater strength to 140 mg/L BOD prior to disposal unless secondary treatment levels are required.” 30 TAC §285.32(f)

What does the TAC say? Defines residential sewage as sewage that has a strength of <300 mg/L BOD Designer should consider if flow equalization is necessary for system to work properly 30 TAC §285.32(f)2, 3

Harris County Onsite Sewage Facility Regulations “Calculations for hydraulic and organic load for both normal and peak flows on all commercial systems shall be provided showing that both organic and hydraulic overloading of the treatment and/or disposal method is prevented.” Commercial maintenance frequency- 12 visits a year

Conclusion Systems that are improperly designed for the waste stream may not protect public health and the environment Photo: http://science.kqed.org/quest/2012/04/27/celebrating-earth-day-in-the-age-of-man/hands-on-a-globe/

Ways to manage high strength wastewater 1. Control at the source Example: scrape plates to reduce FOG 2. Treat to a higher level before discharge Example: install media filter 3. Adjust loading rates according to strength of wastewater Source: Hammerlund and Glotfelty, Maryland Department of the Environment. 2008. Onsite Sewage Disposal of High Strength Wastewater. 17th Annual Maryland Groundwater Symposium 2008.

Questions and/or Comments