Texas Water Development Board€¦ · ro b rts hock ey and ers on t r walk er lu bock vict ri a b t...

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P D K N B M L J O H I C E A G F Groundwater Availability Modeling (GAM) Northern Gulf Coast Aquifer GAM 7 th Stakeholder Advisory Forum July 24, 2003 Contractor: USGS Funding: TWDB, HGCSD &USGS Contract Manager Ali Chowdhury, Ph.D. Texas Water Development Board

Transcript of Texas Water Development Board€¦ · ro b rts hock ey and ers on t r walk er lu bock vict ri a b t...

Page 1: Texas Water Development Board€¦ · ro b rts hock ey and ers on t r walk er lu bock vict ri a b t rp j f n sher an wh el mic h oum t i g win kl er tri n y hem p il wilbar- ger coman-che

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Groundwater Availability Modeling (GAM)

Northern Gulf Coast Aquifer GAM7th Stakeholder Advisory Forum

July 24, 2003Contractor: USGS

Funding: TWDB, HGCSD &USGS

Contract ManagerAli Chowdhury, Ph.D.

Texas Water Development Board

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GAM• Purpose: to develop the best possible

groundwater availability model with the available time and money.

• Public process: you get to see how the model is put together.

• Freely available: standardized, thoroughly documented, and available over the internet.

• Living tools: periodically updated.

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What is a Groundwater Model?

An aquifer in a computer, a tool to estimate field conditions

Effective use of available data and account forcomplexities

Expands our ability to better understand and managethe water resources

Increases prediction accuracy of future events to a level far beyond “best judgement” decisions

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Modeling Protocol

Purpose

Conceptual model

Numerical formulation

Model design

Steady-State ModelCalibration

VerificationTransient Model

(1980-2000)

Comparisonwith

field dataWe are here!

Prediction Runs (2001-2050)Prediction

PostauditField data

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Model Grid

Coarse GridFine Grid

Data Points

data is interpolated (Kriging) between measuredpoints where data is missing

model area discretized into cells

cells are populated with field datawhich are sparse but each modelcell needs a value

higher correlation between points at small sepration distance.kriging prserves the field value at the measurement point

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SandClay

Porosity, Storage, andHydraulic Conductivity

groundwaterflow

High effective porosity/High KStorage

drainable (unconfined)compressible (confined)

High flow velocityBetter water quality

sand grainpore space

Dead endpores

Low effective porosity/low storageLow KLow flow velocityPoor water quality

Kh

Kv

Kh

Kv

Kh

Kv

Porosity: pore space/total voids in a rockStorage: volume of water released per unit

decreases in headHydraulic conductivity: ability to transmit water

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Drawdown Cones in Sand and Clays

Drawdown curve

impervious rock

Ground surface

SWL

impervious rock

Drawdown curve

impervious rock

Ground surface

SWL

impervious rock

SandSandyClay

Q Q

• Broad vs. Steep Drawdown Cones in Sandy vs. Clayey aquifer• Subsidence due to clay compaction

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Gaining vs. losing stream

Ground surfaceStream

(Gaining)

Ground surfaceStream(Losing)

Aquifer

Aquifer

water level

water level

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Package In Out In OutRecharge 42,831,196 -- 44.3% --Streams 52,771,836 83,477,256 54.6% 86.3%

GHB 0 12,673,691 0.0% 13.1%ET -- -- -- --

Reservoirs 1,105,536 0 1.1% 0.0%Drains -- 557,711 -- 0.6%

Total: 96,708,568 96,708,658

Flow (ft^3/day) PercentageWATER BALANCE

Package In Out In OutRecharge 42,831,196 -- 44.3% --Streams 52,771,836 83,477,256 54.6% 86.3%

GHB 0 12,673,691 0.0% 13.1%ET -- -- -- --

Reservoirs 1,105,536 0 1.1% 0.0%Drains -- 557,711 -- 0.6%

Total: 96,708,568 96,708,658

Flow (ft^3/day) PercentageWATER BALANCE

Recharge

• diffuse (direct) - precipitation or irrigation• focused or localized - surface depressions, e.g. lakes or playas• indirect recharge - beneath rivers, lakes• recharge rate depends on rainfall, vegetation, soil type, topography

Recharge for the Gulf Coast aquifer Source Recharge (in/yr) Groschen (1985)

0.06

Ryder (1988) 0 to 6 Dutton and Richter (1990) 0.1 to 0.4 Noble and others (1996) 6 Hay (1999) .00004 to .04 Harden and Associates (2001) 0.1 to 0.2

Average annual rainfall map60 inches in the east to 8 inches

in the west

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Pumping• Historical (pre-

development, 1980-2000)• Predictive (2000-2050)

Categories• municipal• manufacturing• domestic• irrigation• livestock

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What isgroundwateravailability?

• …the amount of groundwater available for use.• safe yield

• average recharge• recharge and change in storage

• systematic depletion

• The State does not decide how much groundwater is available for use: GCDs and RWPGs decide.

• A GAM is a tool that can be used to assess groundwater availability once GCDs and RWPGs decide how to define groundwater availability.

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Do we haveto use GAM?

• Water Code & TWDB rules require that GCDs use GAM information. Other information can be used in conjunction with GAM information.

• TWDB rules require that RWPGs use GAM information unless there is better site specific information available

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• The model– predict water levels and flows in response to

pumping and drought– effects of well fields

• Data in the model– water in storage– recharge estimates– hydraulic properties

• GCDs and RWPGs can request runs

How do weuse GAM?

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Livingtools

• GCDs, RWPGs, TWDB, and others collect new information on aquifer.

• This information can enhance the current GAMs.

• TWDB plans to update GAMs every five years with new information.

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Comments:Contract Manager

[email protected](512)936-0834

www.twdb.state.tx.us/gam

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Hydrogeology, Simulation of Hydrogeology, Simulation of GroundGround--Water Flow, and LandWater Flow, and Land--

Surface Subsidence in the Chicot, Surface Subsidence in the Chicot, Evangeline, and Jasper Aquifers, Evangeline, and Jasper Aquifers,

Houston Area, TexasHouston Area, TexasMark C. Kasmarek, James L. Robinson, and Eric W. StromMark C. Kasmarek, James L. Robinson, and Eric W. Strom

In Cooperation with the Texas Water In Cooperation with the Texas Water Development Board and the HarrisDevelopment Board and the Harris--Galveston Galveston

Coastal Subsidence District Coastal Subsidence District

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TWDB Ground-Water Availability Models in Texas

Modified from TWDB website

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GAM Upper Gulf Coast Aquifer Outcrops

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Stratigraphic and Hydrologic Sections

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2000 Chicot Water-Level Altitude

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2000 Chicot Observed vs. Simulated Target Heads

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2000 Chicot Statistics

• The root mean square error was 24.47 feet between the measured and simulated hydraulic head.

• The maximum hydraulic-head drop across the model layer was 780 feet.

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1977 Chicot Water-Level Altitude

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1977 Chicot Observed vs. Simulated Target Heads

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1977 Chicot Statistics

• The root mean square error was 36.30 feet between the measured and simulated hydraulic head.

• The maximum hydraulic-head drop across the model layer was 599 feet.

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Chicot Well JY-65-18-103

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2000 Evangeline Water-Level Altitude

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2000 Evangeline Observed vs. Simulated Target Heads

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2000 Evangeline Statistics

• The root mean square error was 33.72 feet between the measured and simulated hydraulic head.

• The maximum hydraulic-head drop across the model layer was 594 feet.

Page 32: Texas Water Development Board€¦ · ro b rts hock ey and ers on t r walk er lu bock vict ri a b t rp j f n sher an wh el mic h oum t i g win kl er tri n y hem p il wilbar- ger coman-che

1977 Evangeline Water-Level Altitude

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1977 Evangeline Observed vs. Simulated Target Heads

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1977 Evangeline Statistics

• The root mean square error was 56.54 feet between the measured and simulated hydraulic head.

• The maximum hydraulic-head drop across the model layer was 681 feet.

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Evangeline Well LJ-65-14-602

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2000 Jasper Water-Level Altitude

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2000 Jasper Observed vs. Simulated Target Heads

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2000 Jasper Statistics

• The root mean square error was 33.41 feet between the measured and simulated hydraulic head.

• The maximum hydraulic-head drop across the model layer was 586 feet.

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Jasper Well LJ-65-07-905

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2000 Composite of Observed vs. Simulated Target Heads

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1977 Composite of Observed vs. Simulated Target Heads

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• VOLUMETRIC BUDGET FOR ENTIRE MODEL AT END OF TIME STEP 1 IN STRESS PERIOD 69CUMULATIVE VOLUMES L**3 RATES FOR THIS TIME STEP L**3/T

IN: IN:STORAGE = 848642637824.0000 STORAGE = 22069346.0000

• CONSTANT HEAD = 0.0000 CONSTANT HEAD = 0.0000 • WELLS = 0.0000 WELLS = 0.0000• HEAD DEP BOUNDS = 1.2630E+13 HEAD DEP BOUNDS = 100652320.0000• INTERBED STORAGE = 378706395136.0000 INTERBED STORAGE = 6822997.0000• TOTAL IN = 1.3857E+13 TOTAL IN = 129544664.0000

• OUT: OUT:• STORAGE = 621177274368.0000 STORAGE = 1331763.375• CONSTANT HEAD = 0.0000 CONSTANT HEAD = 0.0000

WELLS = 2.2251E+12 WELLS = 114226888.0000• HEAD DEP BOUNDS = 1.1006E+13 HEAD DEP BOUNDS = 13902051.0000• INTERBED STORAGE = 4949088768.0000 INTERBED STORAGE = 126298.7891• TOTAL OUT = 1.3857E+13 TOTAL OUT = 129587000.0000• IN - OUT = 306184192.0000 IN - OUT = -42336.0000

• PERCENT DISCREPANCY = 0.00 PERCENT DISCREPANCY = -0.03

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Hydrogeology, Simulation of Hydrogeology, Simulation of GroundGround--Water Flow, and LandWater Flow, and Land--

Surface Subsidence in the Chicot, Surface Subsidence in the Chicot, Evangeline, and Jasper Aquifers, Evangeline, and Jasper Aquifers,

Houston Area, TexasHouston Area, TexasMark C. Kasmarek, James L. Robinson, and Eric W. StromMark C. Kasmarek, James L. Robinson, and Eric W. Strom

In Cooperation with the Texas Water In Cooperation with the Texas Water Development Board and the HarrisDevelopment Board and the Harris--Galveston Galveston

Coastal Subsidence District Coastal Subsidence District

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Attendance at the 7th Stakeholder Advisory Forum, Northern Gulf Coast GAM

Participant Affiliation Jim Adams SJRA Bob Pickens Region K, Colorado County Ali Chowdhury TWDB Eric Strom USGS Mark C. Kasmarek USGS Mark Lowry TC&B; H, K and P RWPGs Haskell Simon Coastal Plains GCD Michael Klaus Citizen John Nelson LBG-Guyton Associates

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Q & A’s at the 7th Stakeholder Advisory Forum, Northern Gulf Coast aquifer Groundwater Availability Model, July 24, 2003 Question: Are all of the rivers or just some stretches are gaining in the model area? Response: The recently completed USGS baseflow study suggests that all of the rivers are gaining within the model area. This observation is also supported by model results. USGS will distribute the baseflow study report to the stakeholders who requested the document. Question: How manufacturing pumpage is spatially distributed for the predictive runs? Response: Based on demand numbers provided by the RWPG and distributed around historical uses. Question: The statute and the TWDB rules require that the GCDs and RWPGs use GAM. In the rules “shall” is used, is it being modified by the legislature to offer more flexibility for the GCD’s? Who would be the honest arbiter for deciding what model to use? Response: TWDB approves management plans for the GCDs. The rules allow use of GAM in conjunction with other information. If model results with detailed site-specific information are available that was not included in the GAM, a GCD can provide this for TWDB consideration. Question: Why drawdown presented in Wharton County is not the same as was produced by Dutton model? Drawdown should be presented in the report to make it easier for people to compare water level decline between different time periods. Response: The map shows altitude of water levels but not drawdown. Drawdown maps that would be constructed should show the same levels of drawdown. Drawdown will be reported for each layer by decade. Question: Is the transient calibration complete? Response: Transient calibration is complete unless predictive runs produce results that require revisiting the transient calibration. Question: Is low transmissivity or low storage causing no fluctuations in the hydrographs? Response: We ran simulations with a wide range of transmissivity and storage values and selected the model that produced the best RMS. Question: Can the next SAF meeting after the draft report is submitted so that stakeholders can provide feedback to the consultant after reading the report? Response: Yes. The next SAF meeting will be held after the draft report is submitted at the end of September to facilitate review comments and feedback from the stakeholders. The draft report will also be posted on the web. Question/Comment: One stakeholder stated that some RWPG’s maintain that no additional groundwater models are necessary, as GAMs have already been developed for their area. It was discussed how best to improve the model. Most agreed that model improvements can best occur by collecting more data and populate the data to a finer grid to address local well issues. Models get better as new data is collected and our understanding of the flow system improves.