Allen Hammack, PE US Army Corps of Engineers Engineer R&D Center

Slides:



Advertisements
Similar presentations
Action Effectiveness Monitoring in the Upper Columbia (Chapter 4) Karl M. Polivka, Pacific Northwest Research Station, USDA Forest Service.
Advertisements

6.3 Sediment management options
DESIGN OF AIRFOILS FOR WIND TURBINE BLADES Presented by Parezanovic Vladimir Faculty of Mechanical Engineering Belgrade University.
Upgrade Project.  Old Rexnord bar screen removed and replaced with new Headworks bar screen.  Screenings compactor installed  Chlorine Disinfection.
Lower Yellowstone River Diversion Dam Project – Phase II - Physical Modeling of the Rock Ramp BRT, COE, MTAO Update Meeting November 4, 2010.
Wetland Habitats: EMWMF Haul Road Remediation In 2005 a large haul road was constructed that resulted in loss of wetlands. To compensate for those losses,
NWHA- Panel Discussion “Spawning Better Ideas for Fish Passage”
Permeable Heavy Use Area for Livestock Farms Presentation for Kitsap County DCD, September 28 th, 2006, Lab Test Findings and Calculated Storm Water Performance.
US Army Corps of Engineers BUILDING STRONG ® Methods for Determining Maximum Flood Elevations Landward of Failed Levees: An Example from the Great Missouri.
Reduction of Streamflow From Upstream Ice Formation a.k.a. “Ice Bite” Brian Connelly North Central River Forecast Center Chanhassen, Minnesota.
You manage to disrupt the invasive species’ reproductive cycle, reducing the speed at which it can spread. Remove one die from the invasive species dice.
CHARACTERISTICS OF RUNOFF
ECO ® Series Air Filtration Products Introducing the New ECO III Heavy Duty Air Filtration System.
HEC-RAS US Army Corps of Engineers Hydrologic Engineering Center
Watson Fish Screen By: Bryan Heiner August 2014
Management Issues in the Lake Michigan Basin  Aquatic invasive species  Nutrient enrichment  Beach Health  Contaminants – in Sediments, Fish and Drinking.
Li-Chuan Chen, Marian Muste, and Larry Weber
US Army Corps of Engineers Coastal and Hydraulics Laboratory Engineer Research and Development Center Lower Susquehanna River Watershed Assessment Two.
Wetland Creation Why and How Char Ison and Caleb Asbury.
US Army Corps of Engineers ® Engineer Research and Development Center Coastal and Hydraulics Laboratory Greenup Locks and Dam, Ohio River.
Sanitary Engineering Lecture 11. Storm Water Runoff Storm water runoff is the precipitation which seeps into the ground if precipitation occurs faster.
Blind Pass Project Update Bayous Preservation Assoc. February 9, 2011.
MVS Mainstem Forecast Model Update: NETMISS2 by Joel Asunskis, P.E. Hydraulic Engineer, St. Louis District Water Control U.S. Army Corps Of Engineers October.
US Army Corps of Engineers ® Engineer Research and Development Center 1 Background: High-resolution modeling t = 0.50 s t = 1.0 s t = 2.5 st = 4.5 s Two-phase.
Asian Carp Regional Coordinating Committee [TITLE] [Author] [Date]
US Army Corps of Engineers BUILDING STRONG ® Willamette High Head Bypass August 2014 FPT Brief Jeff Ament, Marie Phillips, Fenton Khan Portland District.
Assessment of Economic Benefits of the North Carolina Floodplain Mapping Program Hydrologic and Hydraulic Case Studies Adapted from a Presentation to NRC.
Modeling in the USACE US Army Corps of Engineers BUILDING STRONG ® Bruce Ebersole U. S. Army Engineer Research and Development Center Coastal & Hydraulics.
- Aquatics - Presented by: Rick Pattenden Mainstream Aquatics Ltd.
US Army Corps of Engineers Coastal and Hydraulics Laboratory Engineer Research and Development Center Lower Susquehanna River Watershed Assessment SedFlume.
Research and Development Inland Waterways Conference 7 March 2007 Improved Hydrodynamic Design/Detection and Evaluation of Scour at Dams John E. Hite,
US Army Corps of Engineers BUILDING STRONG ® Physical and Numerical Model Study of Montgomery Locks and Dam, Ohio River Allen Hammack, Howard Park, Cecil.
US Army Corps of Engineers Detroit District 2012 Training Volunteer Sediment Monitoring Corps & 2-Day Introductory Sediment Course Sediment Strong !
The Lower Mon Project William A. Karaffa, P.E. Project Manager Briefing to Waterways Association of Pittsburgh April 14, 2004.
Water and Climate Change Slobodan P. Simonovic Professor, Department of Civil and Environmental Engineering Director Engineering Studies, Institute for.
HEC-RAS Version 3.1 Overview
Introduction to Chromatography. Introduction Chromatography permit the scientist to separate closely related components of complex mixtures. In all chromatographic.
The Dynamic Earth. BELLWORK Why are greenhouse gases such a major environmental concern? Be specific!
Basic Hydrology & Hydraulics: DES 601 Module 16 Open Channel Flow - II.
MODELING FLOW IN LOCK MANIFOLDS
US Army Corps of Engineers Coastal And Hydraulics Laboratory Engineer Research & Development Center Morganza to the Gulf of Mexico Numerical Model Study.
Basic Hydraulics: Open Channel Flow – II
Thematic assessments based on results from RBMPs Coastal and transitional ecological status & related presures Inland surface waters Hydromorphological.
Glenn E. Moglen Department of Civil & Environmental Engineering Virginia Tech End-of-semester wrap-up CEE 4324/5984 –Open Channel Flow – Lecture 27.
Basic Hydrology & Hydraulics: DES 601
VALVES IN PIPE LINES.
CE 3372 Water Systems Design
Department of Electrical and Computer Engineering
Routing-Hydrologic and Hydraulic
Watershed Origins of Sediment Loads
Stormwater Conveyance Design 2
Module 17: MIXING ZONES A limited area or volume of water where initial dilution of a discharge takes place and where numeric water quality criteria.
Hydraulic and Sediment Handling Performance Assessment of Rani Jamara Kulariya Irrigation Project (RJKIP) by Conjunctive Use of 1D and 3D Simulation Models.
Cara Cowan Watts Graduate Student Biosystems Engineering
Li-Chuan Chen, Marian Muste, and Larry Weber
Waller Creek 8th Street Side Weir CFD Modeling and Simulation
Map-Based Hydrology and Hydraulics
Presented by Arne van der Hout Tom O’Mahoney Tommaso Boschetti
Water, water everywhere
Environmental Law Fall 2018
Li-Chuan Chen, Marian Muste, and Larry Weber
The shapes of stream channels
Review of Flood Reservoir Routing
Marine Biotechnology Lab
HEC-RAS US Army Corps of Engineers Hydrologic Engineering Center
Lake 16 Dam Repair Presentation
Bonneville Washington Shore Fishladder Proposed Entrance Modification for Lamprey at North Downstream Entrance (NDE) Natalie Richards - Project Manager.
A series of vessels of uniform cross section look like letters when viewed face-on. They are 1cm thick, and the corners of the vessels have either whole.
Metropolitan Mayors Caucus March 17, 2015
Environmental Law Fall 2019
Presentation transcript:

Use of a navigation lock as a barrier against the spread of invasive species Allen Hammack, PE US Army Corps of Engineers Engineer R&D Center Coastal and Hydraulics Laboratory September 20, 2017

GLMRIS was created to stop the spread of ANS to the Great Lakes ANS – aquatic nuisance species (particularly Asian carp) Electric barriers, water treatment, navigation locks, etc. Brandon Road Lock

How could a navigation lock be used to prevent the spread of ANS? Upper pool Lower pool likely has ANS (adults, juveniles, eggs, DNA, etc.) Upper pool is clean As vessels/tows transit a lock, can the lock chamber be cleaned or flushed? Lower pool Brandon Road Lock

The lock flushing concepts fall into two categories Lock filling and emptying system Type 1 – existing Type 5 – redesigned to USACE guidance Flow through upstream gate sill Type 3 – series of pipes

The same modeling approach was used for each flushing concept Predict flushing effectiveness/efficiency by tracking flushing flow in chamber AdH Navier-Stokes Moving free surface Previous analytical modeling and literature review provided: Flushing geometries, flushing discharges Flow domain included portion of upper pool, lock chamber to D/S miter gates Chamber: 110 ft X 670 ft X ~15 ft Flushing discharges: Type 1 – 1,350 cfs; Type 3 – 3,000 cfs; Type 5 – 2,600 cfs

A 3D computational mesh was developed for each lock flushing geometry

A 3D computational mesh was developed for each lock flushing geometry

Animations of the concentration plots give an indication of the flushing performance Flushing time = 0 minutes Flushing time = 5 minutes Flushing time = 10 minutes Orange = 100% original lock water, dark blue = 0% original lock water Change from orange to blue indicates original chamber water dilution Concentrations vary in time and space Flushing flow is introduced into lock chamber either through side ports or at upstream end

For Type 1, the original lock chamber water is diluted slowly throughout the chamber 40 minutes of flushing; 1 minute between frames

For Type 5, the original lock chamber water is diluted in the chamber more quickly 40 minutes of flushing; 1 minute between frames

For Type 3, the original lock chamber water is diluted upstream to downstream 40 minutes of flushing; 1 minute between frames

Evaluate lock flushing concepts by monitoring original chamber water concentration How to read a single curve on the plot: Choose a flushing time Move up to a dilution curve Move left to see how much of the lock chamber is at that concentration

Evaluate lock flushing concepts by monitoring original chamber water concentration How to read a single curve on the plot: Choose a flushing time Move up to a dilution curve Move left to see how much of the lock chamber is at that concentration

Evaluate lock flushing concepts by monitoring original chamber water concentration How to read multiple curves at a single time on the plot: Choose a flushing time Move up to a dilution curve Move left to see how much of the lock chamber is at each concentration level

Evaluate lock flushing concepts by monitoring original chamber water concentration How to read multiple curves at a single time on the plot: Choose a flushing time Move up to a dilution curve Move left to see how much of the lock chamber is at each concentration level

The concentration reduction results show how well the lock flushing concepts perform Type 1 Type 5 Type 3 The curves moving to the upper left indicates more efficient flushing Type 5 is more efficient than Type 1 Type 5 has a benefit of reducing the lock filling time A variation of Type 3 will probably be the most efficient at flushing

More information on this study is publicly available http://glmris.anl.gov/brandon-rd/ Appendix E – Hydrology and Hydraulics Allen Hammack allen.hammack@usace.army.mil

Type 1 does not show sufficient flushing in a feasible time Convection-dominated Provides a baseline (“do nothing” case) Clean chamber (99.9% dilution) almost nowhere in chamber after 30 minutes of flushing Poor filling performance (~19 minutes)

Type 5 shows improved but still rather slow flushing performance Convection-dominated Noticeable cleaning (95% dilution) in chamber after 17 minutes of flushing Reduced filling time could compensate for flushing time delay

Type 3 is more efficient in flushing than Types 1 and 5 Advection-dominated Significant cleaning (99.9% dilution) in chamber after 27 minutes of flushing