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Presented By:
Kevin Vought, P.E.
M.S. Civil (Environmental) Engineering
M.S. Nuclear Engineering
15 years experience with a variety of numerical modeling
applications, data processing, 2-D and 3-D visualization, and
programming.
Groundwater / Surface Water
Assessment
Numerous sites investigated
From Northern Canada to Peru; Death Valley to the
wetlands of Florida
o

Investigations for water availability, environmental
restoration, mine dewatering and process supply
Groundwater / Surface Water
Assessment
Types of investigations
Contaminant transport and reactions
Identification and quantification of complex geology
Movement of saltwater / water quality changes
Interaction between surface water and groundwater
Flow through springs and rivers
3-Dimensional Analysis
3-Dimensional Visualization
Pre and Post Processing Tool
Borehole Log Evaluation
Interaction Between Units and Chemicals
Volume Calculations
Convey Information
Used by Numerous Organizations and Companies
Worldwide
3-Dimensional Analysis
• 3-Dimensional Visualization Screen Shots
3-Dimensional Analysis
• 3-Dimensional Visualization Screen Shots
3-Dimensional Analysis
• 3-Dimensional Visualization Screen Shots
3-Dimensional Analysis
• 3-Dimensional Visualization Screen Shots
Groundwater Modeling
• MODFLOW Modeling
– Developed MODFLOW Models for Numerous
Sites Throughout North America
o Locations Include Ontario, Canada; Florida;
New England; Michigan; Ohio; Pennsylvania
o Assisted in development of integrated surface
water / groundwater models in Central,
Southwest, and Southeastern Florida
Groundwater Modeling
MODPATH, MT3DMS, and SEAWAT
MODPATH Simulations to Help Predict
3-D Flow of Water From Source Zones
o

Particle Track Output Analyzed in 3D
Viewers

MT3DMS to account for chemical
reactions and retardation
SEAWAT for variable density
Integrated Surface Water /
Groundwater Modeling
• Integrated Hydrologic Model (IHM)
– Dynamically links HSPF (watershed model)
with MODFLOW
– Attended training sessions for use of the model
– Received personal guidance and training from
one of the developers
Integrated Surface Water /
Groundwater Modeling
• Integrated Hydrologic Model (IHM) cont.
– Reviewed detailed calibration report for the
Integrated Northern Tampa Bay (INTB) Model
o Run with the IHM

– Developed predictive scenarios in the INTB
o Analyzed Minimum Flows and Levels (MFLs)
Integrated Surface Water /
Groundwater Modeling
• MIKE SHE
– Dynamically integrated surface water /
groundwater modeling system
– Oversight of calibration and predictive
scenarios for multiple projects
Broward County IWRMMP
Representative Integrated / Groundwater Project
Project Manager on this Integrated Water Resources
Management Master Plan
$1 million project

Two Primary Tasks
Integrated simulation of canals and Biscayne Aquifer
with MIKE SHE
Simulation of Floridan Aquifer with SEAWAT
IWRMMP – Surficial / Integrated
• Over 200 miles of
canals and waterways
– Dozens of control structures

• MIKE SHE
dynamically linked
these bodies, wetlands,
and the Biscayne
Aquifer
– Enabled evaluation of
impacts from pumping,
canal level settings, etc. as
part of this investigation
IWRMMP - Floridan
• I modified existing
SEAWAT model
• Extent based on maximum
projected drawdown
• Grid refined in urban area
of Broward County
Refined Model Extent

• Additional layer added to
UFA
IWRMMP - Floridan
• 14 layers from ground
surface to the Boulder
Zone
– Aquifers simulated are
UFA, APPZ, and LFA
– Biscayne Aquifer and
Boulder Zone represented
with Constant Heads
Simulated Upper Floridan Water Elevation
IWRMMP - Floridan
• I recalibrated the model to better
calibration statistics than the original
• I developed and ran several predictive
scenarios
− Simulated through 2035
− Evaluated potentiometric surface and TDS
− Injection wells evaluated
IWRMMP - Floridan
• Well locations
− Various
combinations used
in scenarios
− Regional and/or
injection wells not
used in every
scenario
IWRMMP - Floridan
• Broward County production rates
− 80 MGD in 2025
− 103 MGD in 2035

• Broward County injection rates
− 52.75 MGD from 2025 through 2035
IWRMMP - Floridan
• Representative predictive simulations:
pumping at individual utility wellfields
− With and without injection
− Pumping at individual wellfields until 2025
• Additional pumping in regional wellfields after

2025
IWRMMP - Floridan

• Simulated 2035 Drawdown Without Injection
IWRMMP - Floridan

• Simulated 2035 Drawdown With Injection
IWRMMP - Floridan
• Key benefits of injection:
− 2035 drawdown decreases relative to no
injection:
• 14 feet at BCWWS N
• 30 feet at Hollywood
• 20 feet at Davie
IWRMMP - Floridan

• Simulated 2035 Concentration Change Without Injection
IWRMMP - Floridan

• Simulated 2035 Concentration Change With Injection
IWRMMP - Floridan
• Key benefits of injection:
− 2035 concentration decreases relative to no
injection:
• 2,200 mg/L at BCWWS N
• 530 mg/L at Hollywood
• 270 mg/L at Davie
Coastal Modeling
Background and Setting
Bay Joe Wise Headland
Approximately 50 miles southeast of New Orleans
Project area extends from Pass Chaland to Grand Bayou Pass
3 miles of gulf front shoreline
Berm elevations generally +3 to +4 feet NAVD
Loss rate of over 73 acres per year since 1988
Existing breaches along shoreline
Coastal Modeling
Modeling I Conducted for this Investigation
Circulation
Borrow Area Wave Refraction
Inlet Stability (Escoffier Curves)
Cross Shore Sediment Transport
Current and Water Elevation Measurements
Coastal Engineering Consultants, Inc.
Circulation Modeling
Model Description
ADCIRC
2-Dimensional
Finite Volume

Parameters & Calibration
Mesh design
Node spacing
Boundary conditions
Bottom friction
Bathymetric surface / Channel cross section
ADCIRC Mesh for Model Domain
Coastal Engineering Consultants, Inc.
Pass Chaland
Land Outline

*
*

*

Current Meter

*

Tide Gauge

Gulf of Mexico

Bay Joe Wise West Inlet

ADCIRC Model Mesh Near Pass Chaland

Bay Joe Wise

Bayou Chaland

*
Bay Joe Wise

Bay Joe Wise East Inlet

Land Outline

*
*

*

Bastian Bay

*

*

Current Meter

Grand Bayou Pass

Tide Gauge

Gulf of Mexico
ADCIRC Model Mesh Near Grand Bayou Pass
3.000

Gulf Data
Bay Data
2.500

Ideal Match
Gulf Data Trendline

Measured Water Elevation (ft NAVD)

Bay Data Trendline
2.000

1.500

1.000

0.500

0.000
0.000

0.500

1.000

1.500

2.000

Modeled Water Elevation (ft NAVD)

Coastal Engineering Consultants, Inc.

Water Elevation Calibration

2.500

3.000
3
Grand Bayou Pass Data
Pass Chaland Data
Bay Joe Wise East Data
2

Bay Joe Wise West Data
Ideal Match
Grand Bayou Pass Trendline

Measured Water Velocity (ft/s)

Pass Chaland Trendline
1

BJWE Trendline
BJWW Trendline

0

-1

-2

-3
-3

-2

-1

0

1

Modeled Water Velocity (ft/s)

Coastal Engineering Consultants, Inc.

Water Velocity Calibration

2

3
45 Hours
Modeled Water Elevation
(feet NAVD)
2.75
2.50
2.25
2.00
1.75
1.50
1.25
1.00
0.75
0.50

Direction of Flow

Modeled Water Velocity
(feet per second)
3.6
3.0

2.0

1.0

0.0
53 Hours
Modeled Water Elevation
(feet NAVD)
2.75
2.50
2.25
2.00
1.75
1.50
1.25
1.00
0.75
0.50

Direction of Flow

Modeled Water Velocity
(feet per second)
3.6
3.0

2.0

1.0

0.0
58 Hours
Modeled Water Elevation
(feet NAVD)
2.75
2.50
2.25
2.00
1.75
1.50
1.25
1.00
0.75
0.50

Direction of Flow

Modeled Water Velocity
(feet per second)
3.6
3.0

2.0

1.0

0.0
10.0
6.0
2.0
-2.0
-6.0
-10.0
-14.0
-18.0
-22.0
-26.0
-30.0

Bathymetric Surface
(ft NAVD)

Existing Bathymetry
Coastal Engineering Consultants, Inc.
10.0
6.0
2.0
-2.0
-6.0
-10.0
-14.0
-18.0
-22.0
-26.0
-30.0

Bathymetric Surface
(ft NAVD)

Coastal Engineering Consultants, Inc.

Proposed Bathymetry: Alternatives
2 through 4
10.0
6.0
2.0
-2.0
-6.0
-10.0
-14.0
-18.0
-22.0
-26.0
-30.0

Bathymetric Surface
(ft NAVD)

Proposed Bathymetry: Alternative 5
Coastal Engineering Consultants, Inc.
Influence of Alternatives 2 through 4 on Water Velocities

Influence of Alternative 5 on Water Velocities 1
Velocity Vectors
0.5
0.4
0.3
0.2
0.1
0.0
-0.1
-0.2
-0.3
-0.4
-0.5

Water Velocity Change (ft/s)

Note 1: The modified modeled water velocity through the original Bay Joe Wise West Inlet was compared to the
modeled velocity in the new inlet in the velocity comparison for Alternative 5.

Coastal Engineering Consultants, Inc.

Pass Chaland Flow Patterns

4.53 ft/s
0.0 ft/s
Original Land
Outline
Modified Land Outline
Approximate Toe of Fill
0.5
0.6

0.4

0.1
0.2
0.3

-0.1
0.0

-0.2

-0.4
-0.3

Water Velocity Change (ft/s)

Influence of Alternatives 2 through 4 on Water Velocities
Velocity Vectors
4.53 ft/s
0.0 ft/s
Original Land
Outline
Modified Land Outline
Approximate Toe of Fill

Influence of Alternative 5 on Water Velocities

Coastal Engineering Consultants, Inc.

Grand Bayou Pass Flow Patterns
Circulation Results And
Conclusions
Calibration
Velocities within 10ths of feet per second at peaks
Water elevations within 10ths of feet at peaks
Flow patterns match observations

Alternatives Analysis
All alternatives maintain present flow patterns
Slight differences in magnitude of impacts on circulation
from proposed alternative marsh designs
Miami Smelter Expansion FS
Series of 3 evaporation ponds
Designed to evaporate 50% of the scrubber effluent
entering the ponds
Prevent excessive precipitation formation

Primary inputs
Effluent flow rate
Effluent concentrations
Air temperature
Precipitation rate
Evaporation rate
Miami Smelter Expansion FS
Physical pond characteristics (bottom
surface area and side slopes)

Model Root
Screen

100 year 24
hour storm
event and
normal
precipitation

Pond calculations in these containers (i.e.
mass and volume balance)

Total volume and mass
flow into the evaporator
Miami Smelter Expansion FS
Precipitation
Container

Stochastic Precipitation
Inputs
Miami Smelter Expansion FS
Functions Inside “Pond 1” Container
Miami Smelter Expansion FS

Modeled Concentration
Distribution on Next Slide

Dashboard Interaction that Allows Easy Model SetUp for the End User
Miami Smelter Expansion FS

Weight Percent

Total Dissolved Solids Concentration – Pond 3

Date

Output Probability of Outcomes
Stormwater Modeling and Site
Design
• Site Redevelopment and New Site Design
– Properly Sized Retention Ponds
– Designed Drainage Ditch Routing and Sizes,
Drop Structures, Piping Networks, Weirs, and
Other Structures
– Utilized the Interconnected Channel and Pond
Routing Model (ICPR)
Stormwater Modeling and Site
Design
25 Year Storm:

Element Distribution For AdICPR Model - V103 November 2008
Nodes
A Stage/Area
V Stage/Volume
T Time/Stage
M Manhole
Basins
O Overland Flow
U SCS Unit CN
S SBUH CN
Y SCS Unit GA
Z SBUH GA

A: 3050N
W: 305 0W
U: 3050

A: 3000N
T: 33 .301N

A: 3010N

D: 3 000D

Links
P Pipe
W Weir
C Channel
D Drop Structure
B Bridge
R Rating Curve
H Breach
E Percolation
F Filter
X Exfil Trench

C: 3010C
U: 3000

U: 3010

P: 3040P
A: 3020N
U: 3020

A: 30 30N

M : 3040N

P: 3030P

P: 3020P
A: 4530N

U : 3040

U: 30 30

P: 4530P
U: 4530

P: 4540P
A: 45 41N

C: 4 540C

A: 4540N
U: 4540

M: 4580N
C: 45 90C

A: 45 90N
A : 4545N

U: 4580

U: 45 90

C: 4545C
U : 4545

P: 4 580P

A: 4546N

A: 4520N
U: 4520

A: 45 91N

M: 4565N
A: 5035N
P: 456 0P

P: 45 45P

U: 4565
U: 5035
C: 4520C

A : 4592N

C: 4591C
M: 4560N

P: 456 5P

C: 503 5C

A: 4510N
P: 4535P

U: 4560

U: 4510
A: 4521N

A: 45 50N
P: 4590P

A: 5036N

P: 4550 P
U: 45 50

A: 4512N
U: 4512

A: 4535N

C: 4510C
P: 4521P

U: 4535

A: 4575N

C: 4512C

P: 5035P

A: 400 0N

A: 5040N

P: 4575 P
U: 400 0

A: 503 0N

U: 5040

M: 4516N
P: 5020P

U: 4575

P: 5020P_OF

A : 4511N

U: 503 0
D: 5030D
A: 4512B_N

D: 400 0D

P: 4516P

U : 4511
C: 5040A_C
C: 5040B_C

P: 4512P
P: 45 70P

T: 40. 5N

M: 4516A_N

C: 4511_C

A: 5020N
A: 5 040C_N
U: 5020
P: 5040 A_P

A: 45 70A_N

M: 50 40A_M

A: 4511A _N

D: 5040B _D

A: 5010N
U: 5010
C: 45 70_C

P: 5040P
P: 5040B_P
D: 5010D
D: 4511A_D
A: 5041B _N

A: 45 70N

M: 5040B_ M

P: 5041P

U: 45 70

A: 504 1N
D: 5041D

U: 504 1

A: 5041 A_N

C: 504 1C

M: 5041_M
P: 50 41A_P

Interconnected Channel and Pond Routing Model (ICPR) ©2002 Streamline Technologies, Inc.
Stormwater Modeling and Site
Design
Programming
• Many Years Programming with a Variety of
Tools
– FORTRAN
– AWK (Native UNIX Programming Language)
– Microsoft Macros (Excel and PowerPoint)
– Surfer Script Files
Programming

Sample FORTRAN Program I Have Written to Help Process Data
Communication Skills
• Fixed Extremely Frayed Relationship with
Lee County Management at DHI
• Repaired Strained Relationship with
Broward County Management
• Maintained Good Relationships with Other
Clients
Summary
• Groundwater / Surface Water Modeling
Capabilities
– Dewatering / Rerouting of Water
– Contaminant Transport
– Saltwater Intrusion
– Water Supply Availability / Optimization
– Surface Water / Wetland Impacts

• 3-Dimensional Visualization
– Representation of How Natural and Engineered
Site Features Interact
Summary
• GoldSim Modeling
– Stochastic Evaluations

• Hydrodynamic Modeling
– Coastal Tidally Driven Currents and Water
Elevation Changes

• Stormwater Modeling
– ICPR

• Programming
– Several Applications
Questions?

Feel free to contact me with questions at:
k_vought@yahoo.com

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Kevin Vought Select Samples of Water Resource Capability

  • 1. Presented By: Kevin Vought, P.E. M.S. Civil (Environmental) Engineering M.S. Nuclear Engineering 15 years experience with a variety of numerical modeling applications, data processing, 2-D and 3-D visualization, and programming.
  • 2. Groundwater / Surface Water Assessment Numerous sites investigated From Northern Canada to Peru; Death Valley to the wetlands of Florida o Investigations for water availability, environmental restoration, mine dewatering and process supply
  • 3. Groundwater / Surface Water Assessment Types of investigations Contaminant transport and reactions Identification and quantification of complex geology Movement of saltwater / water quality changes Interaction between surface water and groundwater Flow through springs and rivers
  • 4. 3-Dimensional Analysis 3-Dimensional Visualization Pre and Post Processing Tool Borehole Log Evaluation Interaction Between Units and Chemicals Volume Calculations Convey Information Used by Numerous Organizations and Companies Worldwide
  • 5. 3-Dimensional Analysis • 3-Dimensional Visualization Screen Shots
  • 6. 3-Dimensional Analysis • 3-Dimensional Visualization Screen Shots
  • 7. 3-Dimensional Analysis • 3-Dimensional Visualization Screen Shots
  • 8. 3-Dimensional Analysis • 3-Dimensional Visualization Screen Shots
  • 9. Groundwater Modeling • MODFLOW Modeling – Developed MODFLOW Models for Numerous Sites Throughout North America o Locations Include Ontario, Canada; Florida; New England; Michigan; Ohio; Pennsylvania o Assisted in development of integrated surface water / groundwater models in Central, Southwest, and Southeastern Florida
  • 10. Groundwater Modeling MODPATH, MT3DMS, and SEAWAT MODPATH Simulations to Help Predict 3-D Flow of Water From Source Zones o Particle Track Output Analyzed in 3D Viewers MT3DMS to account for chemical reactions and retardation SEAWAT for variable density
  • 11. Integrated Surface Water / Groundwater Modeling • Integrated Hydrologic Model (IHM) – Dynamically links HSPF (watershed model) with MODFLOW – Attended training sessions for use of the model – Received personal guidance and training from one of the developers
  • 12. Integrated Surface Water / Groundwater Modeling • Integrated Hydrologic Model (IHM) cont. – Reviewed detailed calibration report for the Integrated Northern Tampa Bay (INTB) Model o Run with the IHM – Developed predictive scenarios in the INTB o Analyzed Minimum Flows and Levels (MFLs)
  • 13. Integrated Surface Water / Groundwater Modeling • MIKE SHE – Dynamically integrated surface water / groundwater modeling system – Oversight of calibration and predictive scenarios for multiple projects
  • 14. Broward County IWRMMP Representative Integrated / Groundwater Project Project Manager on this Integrated Water Resources Management Master Plan $1 million project Two Primary Tasks Integrated simulation of canals and Biscayne Aquifer with MIKE SHE Simulation of Floridan Aquifer with SEAWAT
  • 15. IWRMMP – Surficial / Integrated • Over 200 miles of canals and waterways – Dozens of control structures • MIKE SHE dynamically linked these bodies, wetlands, and the Biscayne Aquifer – Enabled evaluation of impacts from pumping, canal level settings, etc. as part of this investigation
  • 16. IWRMMP - Floridan • I modified existing SEAWAT model • Extent based on maximum projected drawdown • Grid refined in urban area of Broward County Refined Model Extent • Additional layer added to UFA
  • 17. IWRMMP - Floridan • 14 layers from ground surface to the Boulder Zone – Aquifers simulated are UFA, APPZ, and LFA – Biscayne Aquifer and Boulder Zone represented with Constant Heads Simulated Upper Floridan Water Elevation
  • 18. IWRMMP - Floridan • I recalibrated the model to better calibration statistics than the original • I developed and ran several predictive scenarios − Simulated through 2035 − Evaluated potentiometric surface and TDS − Injection wells evaluated
  • 19. IWRMMP - Floridan • Well locations − Various combinations used in scenarios − Regional and/or injection wells not used in every scenario
  • 20. IWRMMP - Floridan • Broward County production rates − 80 MGD in 2025 − 103 MGD in 2035 • Broward County injection rates − 52.75 MGD from 2025 through 2035
  • 21. IWRMMP - Floridan • Representative predictive simulations: pumping at individual utility wellfields − With and without injection − Pumping at individual wellfields until 2025 • Additional pumping in regional wellfields after 2025
  • 22. IWRMMP - Floridan • Simulated 2035 Drawdown Without Injection
  • 23. IWRMMP - Floridan • Simulated 2035 Drawdown With Injection
  • 24. IWRMMP - Floridan • Key benefits of injection: − 2035 drawdown decreases relative to no injection: • 14 feet at BCWWS N • 30 feet at Hollywood • 20 feet at Davie
  • 25. IWRMMP - Floridan • Simulated 2035 Concentration Change Without Injection
  • 26. IWRMMP - Floridan • Simulated 2035 Concentration Change With Injection
  • 27. IWRMMP - Floridan • Key benefits of injection: − 2035 concentration decreases relative to no injection: • 2,200 mg/L at BCWWS N • 530 mg/L at Hollywood • 270 mg/L at Davie
  • 28. Coastal Modeling Background and Setting Bay Joe Wise Headland Approximately 50 miles southeast of New Orleans Project area extends from Pass Chaland to Grand Bayou Pass 3 miles of gulf front shoreline Berm elevations generally +3 to +4 feet NAVD Loss rate of over 73 acres per year since 1988 Existing breaches along shoreline
  • 29. Coastal Modeling Modeling I Conducted for this Investigation Circulation Borrow Area Wave Refraction Inlet Stability (Escoffier Curves) Cross Shore Sediment Transport
  • 30. Current and Water Elevation Measurements Coastal Engineering Consultants, Inc.
  • 31. Circulation Modeling Model Description ADCIRC 2-Dimensional Finite Volume Parameters & Calibration Mesh design Node spacing Boundary conditions Bottom friction Bathymetric surface / Channel cross section
  • 32. ADCIRC Mesh for Model Domain Coastal Engineering Consultants, Inc.
  • 33. Pass Chaland Land Outline * * * Current Meter * Tide Gauge Gulf of Mexico Bay Joe Wise West Inlet ADCIRC Model Mesh Near Pass Chaland Bay Joe Wise Bayou Chaland *
  • 34. Bay Joe Wise Bay Joe Wise East Inlet Land Outline * * * Bastian Bay * * Current Meter Grand Bayou Pass Tide Gauge Gulf of Mexico ADCIRC Model Mesh Near Grand Bayou Pass
  • 35. 3.000 Gulf Data Bay Data 2.500 Ideal Match Gulf Data Trendline Measured Water Elevation (ft NAVD) Bay Data Trendline 2.000 1.500 1.000 0.500 0.000 0.000 0.500 1.000 1.500 2.000 Modeled Water Elevation (ft NAVD) Coastal Engineering Consultants, Inc. Water Elevation Calibration 2.500 3.000
  • 36. 3 Grand Bayou Pass Data Pass Chaland Data Bay Joe Wise East Data 2 Bay Joe Wise West Data Ideal Match Grand Bayou Pass Trendline Measured Water Velocity (ft/s) Pass Chaland Trendline 1 BJWE Trendline BJWW Trendline 0 -1 -2 -3 -3 -2 -1 0 1 Modeled Water Velocity (ft/s) Coastal Engineering Consultants, Inc. Water Velocity Calibration 2 3
  • 37. 45 Hours Modeled Water Elevation (feet NAVD) 2.75 2.50 2.25 2.00 1.75 1.50 1.25 1.00 0.75 0.50 Direction of Flow Modeled Water Velocity (feet per second) 3.6 3.0 2.0 1.0 0.0
  • 38. 53 Hours Modeled Water Elevation (feet NAVD) 2.75 2.50 2.25 2.00 1.75 1.50 1.25 1.00 0.75 0.50 Direction of Flow Modeled Water Velocity (feet per second) 3.6 3.0 2.0 1.0 0.0
  • 39. 58 Hours Modeled Water Elevation (feet NAVD) 2.75 2.50 2.25 2.00 1.75 1.50 1.25 1.00 0.75 0.50 Direction of Flow Modeled Water Velocity (feet per second) 3.6 3.0 2.0 1.0 0.0
  • 41. 10.0 6.0 2.0 -2.0 -6.0 -10.0 -14.0 -18.0 -22.0 -26.0 -30.0 Bathymetric Surface (ft NAVD) Coastal Engineering Consultants, Inc. Proposed Bathymetry: Alternatives 2 through 4
  • 42. 10.0 6.0 2.0 -2.0 -6.0 -10.0 -14.0 -18.0 -22.0 -26.0 -30.0 Bathymetric Surface (ft NAVD) Proposed Bathymetry: Alternative 5 Coastal Engineering Consultants, Inc.
  • 43. Influence of Alternatives 2 through 4 on Water Velocities Influence of Alternative 5 on Water Velocities 1 Velocity Vectors 0.5 0.4 0.3 0.2 0.1 0.0 -0.1 -0.2 -0.3 -0.4 -0.5 Water Velocity Change (ft/s) Note 1: The modified modeled water velocity through the original Bay Joe Wise West Inlet was compared to the modeled velocity in the new inlet in the velocity comparison for Alternative 5. Coastal Engineering Consultants, Inc. Pass Chaland Flow Patterns 4.53 ft/s 0.0 ft/s Original Land Outline Modified Land Outline Approximate Toe of Fill
  • 44. 0.5 0.6 0.4 0.1 0.2 0.3 -0.1 0.0 -0.2 -0.4 -0.3 Water Velocity Change (ft/s) Influence of Alternatives 2 through 4 on Water Velocities Velocity Vectors 4.53 ft/s 0.0 ft/s Original Land Outline Modified Land Outline Approximate Toe of Fill Influence of Alternative 5 on Water Velocities Coastal Engineering Consultants, Inc. Grand Bayou Pass Flow Patterns
  • 45. Circulation Results And Conclusions Calibration Velocities within 10ths of feet per second at peaks Water elevations within 10ths of feet at peaks Flow patterns match observations Alternatives Analysis All alternatives maintain present flow patterns Slight differences in magnitude of impacts on circulation from proposed alternative marsh designs
  • 46. Miami Smelter Expansion FS Series of 3 evaporation ponds Designed to evaporate 50% of the scrubber effluent entering the ponds Prevent excessive precipitation formation Primary inputs Effluent flow rate Effluent concentrations Air temperature Precipitation rate Evaporation rate
  • 47. Miami Smelter Expansion FS Physical pond characteristics (bottom surface area and side slopes) Model Root Screen 100 year 24 hour storm event and normal precipitation Pond calculations in these containers (i.e. mass and volume balance) Total volume and mass flow into the evaporator
  • 48. Miami Smelter Expansion FS Precipitation Container Stochastic Precipitation Inputs
  • 49. Miami Smelter Expansion FS Functions Inside “Pond 1” Container
  • 50. Miami Smelter Expansion FS Modeled Concentration Distribution on Next Slide Dashboard Interaction that Allows Easy Model SetUp for the End User
  • 51. Miami Smelter Expansion FS Weight Percent Total Dissolved Solids Concentration – Pond 3 Date Output Probability of Outcomes
  • 52. Stormwater Modeling and Site Design • Site Redevelopment and New Site Design – Properly Sized Retention Ponds – Designed Drainage Ditch Routing and Sizes, Drop Structures, Piping Networks, Weirs, and Other Structures – Utilized the Interconnected Channel and Pond Routing Model (ICPR)
  • 53. Stormwater Modeling and Site Design 25 Year Storm: Element Distribution For AdICPR Model - V103 November 2008 Nodes A Stage/Area V Stage/Volume T Time/Stage M Manhole Basins O Overland Flow U SCS Unit CN S SBUH CN Y SCS Unit GA Z SBUH GA A: 3050N W: 305 0W U: 3050 A: 3000N T: 33 .301N A: 3010N D: 3 000D Links P Pipe W Weir C Channel D Drop Structure B Bridge R Rating Curve H Breach E Percolation F Filter X Exfil Trench C: 3010C U: 3000 U: 3010 P: 3040P A: 3020N U: 3020 A: 30 30N M : 3040N P: 3030P P: 3020P A: 4530N U : 3040 U: 30 30 P: 4530P U: 4530 P: 4540P A: 45 41N C: 4 540C A: 4540N U: 4540 M: 4580N C: 45 90C A: 45 90N A : 4545N U: 4580 U: 45 90 C: 4545C U : 4545 P: 4 580P A: 4546N A: 4520N U: 4520 A: 45 91N M: 4565N A: 5035N P: 456 0P P: 45 45P U: 4565 U: 5035 C: 4520C A : 4592N C: 4591C M: 4560N P: 456 5P C: 503 5C A: 4510N P: 4535P U: 4560 U: 4510 A: 4521N A: 45 50N P: 4590P A: 5036N P: 4550 P U: 45 50 A: 4512N U: 4512 A: 4535N C: 4510C P: 4521P U: 4535 A: 4575N C: 4512C P: 5035P A: 400 0N A: 5040N P: 4575 P U: 400 0 A: 503 0N U: 5040 M: 4516N P: 5020P U: 4575 P: 5020P_OF A : 4511N U: 503 0 D: 5030D A: 4512B_N D: 400 0D P: 4516P U : 4511 C: 5040A_C C: 5040B_C P: 4512P P: 45 70P T: 40. 5N M: 4516A_N C: 4511_C A: 5020N A: 5 040C_N U: 5020 P: 5040 A_P A: 45 70A_N M: 50 40A_M A: 4511A _N D: 5040B _D A: 5010N U: 5010 C: 45 70_C P: 5040P P: 5040B_P D: 5010D D: 4511A_D A: 5041B _N A: 45 70N M: 5040B_ M P: 5041P U: 45 70 A: 504 1N D: 5041D U: 504 1 A: 5041 A_N C: 504 1C M: 5041_M P: 50 41A_P Interconnected Channel and Pond Routing Model (ICPR) ©2002 Streamline Technologies, Inc.
  • 54. Stormwater Modeling and Site Design
  • 55. Programming • Many Years Programming with a Variety of Tools – FORTRAN – AWK (Native UNIX Programming Language) – Microsoft Macros (Excel and PowerPoint) – Surfer Script Files
  • 56. Programming Sample FORTRAN Program I Have Written to Help Process Data
  • 57. Communication Skills • Fixed Extremely Frayed Relationship with Lee County Management at DHI • Repaired Strained Relationship with Broward County Management • Maintained Good Relationships with Other Clients
  • 58. Summary • Groundwater / Surface Water Modeling Capabilities – Dewatering / Rerouting of Water – Contaminant Transport – Saltwater Intrusion – Water Supply Availability / Optimization – Surface Water / Wetland Impacts • 3-Dimensional Visualization – Representation of How Natural and Engineered Site Features Interact
  • 59. Summary • GoldSim Modeling – Stochastic Evaluations • Hydrodynamic Modeling – Coastal Tidally Driven Currents and Water Elevation Changes • Stormwater Modeling – ICPR • Programming – Several Applications
  • 60. Questions? Feel free to contact me with questions at: k_vought@yahoo.com