ground-water resources and management of the … · management of the guadalupe groundwater...
TRANSCRIPT
(
GROUND-WATER RESOURCES AND MANAGEMENT OF THE
GUADALUPE GROUNDWATER CONSERVATION DISTRICT
Prepared For
Guadalupe County Groundwater Conservation District
Seguin, Texas
August 2002
LBG-GUYTON ASSOCIATES Professional Ground-Water and Environmental Services
1101 S. Capital of Texas Highway, Suite B-220 Austin, Texas 78746
DECE,vEn n AP~ iO 2 2012 U
BY: . \,pm .•
CHARLES W. KREITLER W. JOHN SEIFERT, JR. JOHN B. ASHWORTH JAMES BEACH BRUCE K. DARLING
BRAD L. CROSS ANDREW C.A. DONNELLY ERIC K. McALPINE JOHN W. NELSON KRISTlE L, PERSKY ALLAN R. STANDEN WILLIAM G. STEIN
Mr. Robin Dwyer
LBG-GUYTON ASSOCIATES PROFESSIONAL GROUND-WATER AND
ENVIRONMENTAL ENGINEERING SERVICES
1101 S, CAPITAL OF TEXAS HIGHWAY SUlTEB-220
AUSTIN, TX 78746-6437 512-327-9640
FAX 512-327-5573
August 14,2002
Guadalupe County Groundwater Conservation District 109 W. Court Seguin, TX 78155
Dear Mr. Dwyer:
ROBERT LAMONICA R,O, SLAYBACK WILLIAM K. BECKMAN DAN C, BUZEA J. KEVIN POWERS JOI·IN NAsa, JR. FRANK J, GETCHELL JEFFREY B. LENNOX
WILLIAM B. KLEMT
Transmitted herewith is our report, "Ground-Water Resources and Management of the Guadalupe County Groundwater Conservation District."
firm.
a call.
This report was prepared principally by me with some assistance from other of our
If you have any questions regarding the report or results of the study, please give me
Yours sincerely,
LBG-GUYTON ASSOCIATES
William B. Klemt Senior Consultant
A Division of Leggette, Brashears & Graham, Inc.
( )
()
TABLE OF CONTENTS
INTRODUCTION ......................................................................................................................... 1
Location and Extent of Study area .............................................................................................. 1 Purpose and Scope ....................................................................................................................... 1 Aclmowledgements ..................................................................................................................... 2
CARRIZO-WILCOX AQUIFER ................................................................................................ 2
Water-Bearing Strata ................................................................................................................... 2 Recharge, Discharge and Movement ........................................................................................... 3 Hydraulic Characteristics ............................................................................................................ 4 Chemical Quality ......................................................................................................................... 4
GROUND-WATER A V AILABILITy ......................................................................................... 5
GROUND .. WATER MANAGEMENT ....................................................................................... 6
Ground-Water Management Considerations ............................................................................... 6 Drought Contingency Planning ................................................................................................... 7
CONCLUSIONS AND RECOMMENDATIONS ...................................................................... 8
Monitoring ................................................................................................................................... 8 I
\ Ground-Water Management Considerations ............................................................................... 9 Ground-Water Management Zones ............................................................................................. 9 Water Marketing ........................................................................................................................ 10 Drought Contingency Planning ................................................................................................. 11
SELECTED REFERENCES ..................................................................................................... 13
LBG-GUYTON ASSOCIATES
Table 1
Figure
TABLE (at end of report)
Proposed Water-Level Observation Wells
LIST OF FIGURES (at end of report)
1 Texas Water Development Board Water Level Observation Wells
2 Texas Water Development Board Results of Water-Chemistry Analyses of Ground Water from the Carrizo-Wilcox Aquifer (1 970-Present)
3 Generalized Geologic Section A-A'
4 Approximate Altitude of the Base of the Carrizo-Wilcox Aquifer
5 Approximate Water Saturated Thickness of the Carrizo-Wilcox Aquifer
6 Approximate Altitude of the Base of the Carrizo Aquifer
7 Approximate Altitude of the Top of the Can'izo Aquifer
8 Approximate Water Saturated Thickness of the Carrizo Aquifer In Guadalupe County
9 Approximate Altitude of Water Levels in the Can'izo-Wilcox Aquifer, Year 2002
10 Approximate Artesian Pressure Head Above the Top of the Carrizo Aquifer
(
(
(
LBG-GUYTON ASSOCIATES
/
GROUND-WATER RESOURCES AND MANAGEMENT OF THE GUADALUPE COUNTY GROUNDWATER CONSERVATION DISTRICT
INTRODUCTION
The anticipated future water demands of Schertz and Seguin, Texas, and other small
communities in Guadalupe County may require some sources other than the Edwards aquifer and
surface water from the Guadalupe River. One possible alternative is the development of wells in
Guadalupe County, which would supply water from the Carrizo-Wilcox aquifer. Previous
studies by the Texas Water Development Board and others have shown that significant quantities
of water (greater than 10,000 acre-feet per year) maybe able to be developed from the aquifer
for municipal supplies. Management and protection of the ground-water resources of the
Carrizo-Wilcox aquifer in Guadalupe County is the responsibility of the Guadalupe County
Groundwater Conservation District.
Location and Extent of Study Area
The study area consists of the southeastern portion of Guadalupe County where the
CaITizo-Wilcox aquifer is present. It consists of approximately one-half of Guadalupe County.
Figures 1 and 2 show following: (a) the location of the District; (b) aerial extent of the Carrizo
Wilcox aquifer; and (c) water wells utilized by the Texas Water Development Board to track
changes in water levels and water quality in the Carrizo-Wilcox aquifer.
Purpose and Scope
The primary objective of this study is to improve the basic understanding of the ground
water conditions in the District and identify possible management strategies in order to regulate
the production of ground-water from the CaITizo-Wilcox aquifer to ensure adequate water for the
future.
The scope of work includes the following: (a) review readily available ground-water data
and reports for that portion of Guadalupe County underlain by the Carrizo-Wilcox aquifer; (b)
estimate the aquifer's parameters (penneability, transmissivity, and storage); (c) make estimates
of recharge to the aquifer; (d) conduct a work shop with the District's Board Members to
( improve the basic understanding of the hydrogeology of the aquifer in Guadalupe County; (e)
LBG-GUYTON ASSOCIATES
-2-
identify wells which may be used by the District to track changes in water levels; and (f) prepare
a report which summarizes the findings and makes recommendations with regard to management
of the District.
Acknowledgements
We wish to express our grateful acknowledgement to all individuals and organizations
who participated in this study. The cooperation of federal and state agencies, especially the
Texas Water Development Board, is also gratefully acknowledged.
Special acknowledgement is extended to Mr. Craig Caldwell and Mr. Randy Williams of
the Texas Water Development Board. These men generously provided basic data, technical
info=ation, and advice, which contributed toward the successful completion of this study.
Finally, appreciation is expressed to Mr. Ronald Naumann, Mr. Hilmar Blumberg, and
Mr. Robin Dwyer of the Guadalupe County Groundwater Conservation District. Their helpful
cooperation and interest contributed toward the successful completion of this investigation and a
better understanding of the Carrizo-Wilcox aquifer in Guadalupe County.
CARRIZO-WILCOX AQUIFER
The name "Carrizo" was first applied to the thick, massive sand beds that overlie the
sands, silts and clays of the Wilcox Group in the vicinity of Carrizo Springs, Texas around the
tum of the 19th century. Because the sands of the Wilcox Group are hydraulically connected
with the Carrizo Sand in Guadalupe County, the te= "Carrizo-Wilcox aquifer" is often used.
Water-Bearing Strata
The water-bearing strata of the Carrizo-Wilcox aquifer are marine and continental in
origin and consist mainly of cross-bedded river sand, beach sand, silt, clay, and lignite. These
sediments were deposited by large, fluvial-deltaic river systems which were sourced in the
Rocky Mountains and Ouachita-Arbuckle Mountains (Ayers and Lewis, 1985). Figure 3 shows
the position of the aquifer in the subsurface and geologic fo=ations, which bound the aquifer
above and below. Overlying the Carrizo Sand are the clays and interbedded glauconitic sands of
(
(
LBG-GUYTON ASSOCIATES
- 3 -
the Reklaw FOlmation. Underlying the Wilcox are the clays and shales of the Midway
( formation.
(
(
The San Marcos Arch, which generally trends northwest-southeast parallel to the
Guadalupe and Caldwell County line, is a structural high which affected the deposition and
faulting of the Carrizo-Wilcox in Guadalupe County. The aquifer thins over the arch and
thickens to the north and south. The altitude of the base of the Canizo-Wilcox aquifer with the
associated faulting and the water-saturated thickness of the aquifer is shown on Figures 4 and 5,
respectively.
In Guadalupe County, the Carrizo aquifer is the preferred source of ground water with
only minor amounts of water being withdrawn from the sands and clays of the Wilcox. The
altitude of the base and top of the aquifer and its water-saturated thickness are shown on Figures
6, 7, and 8, respectively.
Recharge, Discharge and Movement
The Camzo-Wilcox aquifer is recharged by precipitation and certain situations by
seepage from lakes, streams, and rivers crossing the outcrop area. Significant factors which
control the amount of water recharged include: topography of the land surface, amount and kind
of vegetative cover, soil characteristics and hydraulic conductivity (penneability) of the rocks
and soils exposed in the outcrop. Surface topography exerts a strong control on ground-water
movement within the aquifer, with recharge occurring in the outcrop along drainage divides and
moving down gradient into the aquifer and/or discharging to topographic lows along river basins.
The percentage of the average annual precipitation rate that enters the Camzo-Wilcox .
outcrop and is transmitted downdip is often referred to as effective recharge. Calculations made
by Shafer (1966) indicate the effective recharge is on the order of an inch per year or
approximately three percent of the average annual precipitation rate in Guadalupe County. The
estimated I inch of effective recharge applied to the outcrop of the Camzo-Wilcox aquifer in
Guadalupe County is roughly equivalent to 20,000 acre-feet per year. However, it is estimated
that approximately one-half or more of the 20, 000 acre-feet is recharged in the outcrop ofthe
Camzo aquifer. This is roughly 2 to 3 inches of the average annual precipitation rate applied to
the outcrop of the Canizo.
Ground water in the Carrizo-Wilcox aquifer moves downward from the recharge zone
LBG-GUYTON ASSOCIATES
- 4-
(outcrop) to the zone of saturation and then generally in the direction of the water-level gradient
to points of discharge (wells, livers, springs, seeps, etc.). On the order of 1,500 acre-feet of
ground water is presently being pumped from the aquifer.
Figure 9 illustrates the water-level surface of the aquifer, which is an imaginary surface
that everywhere coincides with the static water level in the aquifer. These water levels indicate
the general direction of ground-water movement is southeastward toward Gonzales County and
that there is some flow toward the Guadalupe and San Marcos Rivers. Losses of potential
recharge include seepage losses on the outcrop and evapotranspiration.
Hydraulic Characteristics
An aquifer's hydraulic characteristics are generally described in terms of its coefficients
of transmissivity and storage. These are determined generally for the Carrizo-Wilcox aquifer by
conducting pumping tests in selected wells and from well performance tests conducted by water
well ddlling and servicing companies. Transmissivity and storage are a measure of an aquifer's
ability to transmit and store water, and can be used to determine proper well spacing,
interference between pumping wells and to predict water-level drawdowns around pumping
wells.
Little is known about the hydraulic characteristics of the Wilcox underlying Guadalupe
County, pdncipally because of the lack of suitable wells in which to observe these
charactedstics. A few well pumping rates of as high as 400 to 500 gallons per minute (gpm)
have been reported. However, large wells are the exception as most of the inventoried Wilcox
wells are reported to have small well yields.
Chemical Quality
Large well pumping rates ranging from 500 to as high as 1,500 gpm can be expected
from the Carlizo aquifer in southeastern Guadalupe County. An aquifer test which was
conducted in southeastern Guadalupe County where the Camzo aquifer is under artesian
conditions indicates the transmissivity of the Camzo is on the order of 40,000 to 50,000 gallons
per day per foot (gpd/ft). In the outcrop where the Camzo is under water-table conditions, the
transmissivity of the aquifer is less. Coefficients of storage for the Carrizo aquifer probably
range from 0.0001 to 0.001 and from 0.10 to 0.30 in the artesian and outcrop portions of
(
(
(
LBG-GUYTON ASSOCIATES
- 5 -
Guadalupe County, respectively. The outcrop and artesian portions of the Carrizo-Wilcox
C aquifer are shown on Figure 10.
(
(
In general, water quality of the Carrizo aquifer in Guadalupe County is good and meets
the National Primary Drinking Water Regulations Standards required for public health.
However, secondary standards for pH and iron may not be met. Water exceeding secondary
standards poses an aesthetic problem, not a health risk. Additionally, hydrogen sulfide and
methane gas may be found locally within the Carrizo aquifer.
The water chemistry of the Wilcox is quite variable, and in general, the water quality is
not as good as the Can'izo aquifer (Figure 2). Dissolved solids, chloride, and sulfate can be
much higher and may not meet state standards.
Some of the local variability seen in the water-chemistry results for the aquifer
(especially the Wilcox) are probably dependent on proper well completions and sampling
procedures used. For comparison purposes, the water chemistry values shown on Figure 2 can
be compared with the Texas Natural Resource Conservation Commission's (TNRCC) Interim
Use Drinking-Water Standards for Public Health. TNRCC's standards are as follows: a)
dissolved solids, 1,000 milligrams per liter (mg/l); b) chloride, 300 mg/l; and c) sulfate, 300
mg/l.
GROUND-WATER AVAILABILITY
The amount of ground water that can be developed by wells from the Carrizo-Wilcox
aquifer in the District on a long-term basis is directly related to the ability of the aquifer to
transmit water from the outcrop to points of discharge. In addition to the aquifer's effective
recharge, there is the assumption that a small amount of water in storage can be withdrawn on a
constant annual basis.
The amount of ground water from the Carrizo Wilcox aquifer which may be utilized for
future development for the next twenty (20) years without causing excessive water-level declines
within the District is approximately 12,600 acre-feet per year (acre-ftlyr) less the 1,500 acre-ftlyr
which is presently being pumped (public water supplies, almost 1,000 acre-ftlyr). Projected
ground-water demands on the aquifer are expected to double by the year 2020 (about 3,000 acre-
LEG-GUYTON ASSOCIATES
- 6 -
ft/yr). Therefore, on the order of 10,000 acre-ftlyr is available for future development over the
~W~. (
The 12,600 acre-ft/yr estimate was derived from tabulations prepared by Muller and Price
(1979). The most favorable area to develop this water is from the Ca11'izo aquifer in southeastern
Guadalupe County where artesian conditions exist.
GROUND-WATER MANAGEMENT
The Guadalupe County Groundwater Conservation District has adopted preliminary
rules, and the Texas Water Development Board is presently reviewing the District's
"Management Plan". The District's "Drought Management Plan" will be developed within
approximately one year. The remarks below are pertinent to ground-water management within
the District.
Ground-Water Management Considerations
The Guadalupe County Groundwater Conservation District has been given great C flexibility in determining what powers they will exercise in the regulation of large wells (wells
which produce over 25,000 gallons per day). This allows for a strong active district to serve the
needs of Guadalupe County. The following are important considerations and activities with
regard to what the District may do in developing a regulatory strategy: (a) well spacing and
ground-water production may be regulated; (b) require permits for drilling, equipping and
completion of water wells; (c) maintain water-well drilling, production, rainfall, water-level, and
water-chemistry records; and (d) commission ground-water studies.
One of the District's important goals is to limit water-level declines in the Can'izo-Wilcox
aquifer. It has been proposed that the District regulate ground-water production in order to meet
this goal in one of two ways: (a) allow 2 acre-feet of water per year to be produced per acre for
large wells; or (b) allow a much smaller ground-water allocation per acre in order that all
properties within the District would have a ground-water allowable for large wells. In each case,
the ground-water allowable could be used or sold should there be a water market. However, in
each case, the District should limit total ground-water production to 12,600 acre-feet per year (
LBG-GUYTON ASSOCIATES
- 7 -
from the aquifer.
( In the first case, only a limited number of property owners located in southeastern
(
.I
Guadalupe County would be able to utilize their allowable for production or take advantage of
the water market. This is because southeastern Guadalupe County is the most favorable area for
ground-water production from the Carrizo aquifer. At this location, the Carrizo consists mostly
of fine to coarse, loose sand, aud is capable of very large well pumping rates. The number of
surface acres which may be presently utilized for this purpose would be about 5,000 acres.
In the second case, all of the landowners located over the Carrizo-Wilcox aquifer would
be able to utilize their allowable or participate in the water market. However, those areas not
located in southeastern Guadalupe County are not as favorable for ground-water production and
their allowable would less than 1 inch per acre to either sell or use.
Drought Contingency Planning
A "good" drought contingency plan is one that is tailored to the unique conditions and
circumstances of the District. There is a stepwise process that can be followed to develop au
effective drought contingency plan for the Carrizo-Wilcox aquifer to satisfy state requirements.
There are six basic steps, which are as follows:
I. Involve the public in the development of the plan. This can be done through public
notification and information about the plan, and public involvement in plan
development.
2. Assess the District's vulnerability to drought and define criteria for initiating or
terminating (triggering criteria) drought response measures. The pIau should include
specific criteria for determining when water supply, water demand, or other
conditions warrant implementation or termination of drought response measures. For
example, implementation of drought response measures might be initiated when
water levels are declining at a rate faster than expected or water demand equals or
exceeds some value or percentage ofthe District's production allowable (12,600 ac
ftlyr) over some defined period of time (e.g., trigger levels beginning when daily
water demand exceeds 60 percent oflarge well capacity or the Distlict's production
LBG-GUYTON ASSOCIATES
- 8 -
allowable).
3. Detennine drought response measures. This could include curtailment ofpelmitted
production rates for large wells and/or mandatory restrictions on certain water uses
within the District.
4. Design a multistage plan. The plan should provide for the implementation of drought
response measures in successive stages (usually three to five stages) geared to the
severity of the situation. For example, the District may increase public awareness
during mild conditions up to reducing pennitted production rates for large wells
during critical conditions.
5. Adopt the plan through administrative rules by the District's Board of Directors.
6. Review and/or update the plan at least every 5 years.
CONCLUSIONS AND RECOMMENDATIONS
The Carrizo-Wilcox aquifer's ground-water resources in Guadalupe County have only
been partially developed. On the order of 12,600 acre-ftlyr of ground water is available,
primarily from the aquifer. In the area of the Wilcox outcrop, most wells are domestic-stock
wells with small well yields. However, present pump age is on the order of 1,500 acre-ft/yr from
the Carrizo-Wilcox aquifer and is expected to increase to about 3,000 acre-ftlyr by the year 2020.
Therefore, on the order of 10,000 acre-ftlyr over the next 20 years is available for future
development, primarily from the Canizo aquifer.
Monitoring
The District should establish a water-level program in order to monitor water-level
changes in the Carrizo-Wilcox aquifer. It is recommended that five wells be selected and
measured in January and August of each year. The location and records of six wells, which may
(
(
(
LEG-GUYTON ASSOCIATES
- 9-
be suitable, are shown on Figure 1 and the attached table. However, these wells will need to be
inventoried before it can be detennined they are suitable. The District's measurements, when
combined with the Texas Water Development Board's water-level program measurements, over
the next 5 years should provide the necessary infonnation to define unacceptable water-level
declines, drought conditions, and water-level drought triggers in order to prepare a drought
contingency plan.
In addition to a water-level program, the District should develop a rainfall monitoring
program. The rainfall stations should be located on or close to the outcrop of the Carrizo aquifer.
These stations may help in detennining drought conditions and estimating the recharge to the
Carrizo within the District.
Ground-Water Management Considerations
The District's Board of Directors, in developing the District's management and
regulatory ground-water program, should promote water conservation, provide public
infonnation, issue water-well pennits, take enforcement action where necessary, and cooperate
with adjacent ground-water districts and other water agencies.
( In administering a permit program that limits pumping from the Carrizo-Wilcox aquifer
(
to 12,600 acre-ftJyr, the Board of Directors should be aware that historical and present pump age
from the Carrizo aquifer in Guadalupe County and adjacent counties are causing regional water
level declines of about one (1) foot per year within the District. Increased future development of
the Carrizo in these areas will increase the rate of regional water-level decline. In addition, it is
expected that future development of the Carrizo aquifer will have little impact on the Wilcox
aquifer within the District. The Board should also consider such things as spacing, production,
water-level declines in the vicinity of the proposed well and neighbors' wells, and location within
or distance to the Carrizo outcrop. The Board should also be ready to deny a water-well permit
when the permit application is not in accordance with the rules and guidelines of the District and
to reduce permitted pumping rates when water levels are declining at a rate faster than
anticipated.
LBG-GUYTON ASSOCIATES
- 10 -
Ground-Water Management Zoues
There are three possible management zones within the District. These zones are as (
follows: (a) the outcrop of the Wilcox; (b) the outcrop of the Carrizo and those areas down dip
where the aquifer is under water-table conditions; and (c) those areas where the Carrizo aquifer
is under artesian conditions. Figure 10 generally shows these areas.
The outcrop of the Wilcox should not require a great deal of management effort. This is
because, in general, the aquifer will not support large-capacity wells, and the water quality is not
as good as the Carrizo. For management purposes, new and existing wells should be permitted
so that the District knows where they are and about how much they are pumping on an annual
basis.
Where the Carrizo aquifer is under water-table conditions (outcrop and areas immediately
down-dip of the outcrop), management will be required in order that the aquifer in the outcrop is
not dewatered extensively. The District should detennine how much water levels will be
allowed to decline and over what time period. Perhaps a maximum of 50 tol00 feet of water
level decline could be tolerat(jd over a period of25 years (about 2 to 4 feet per year). In order to
manage the zone in this way, the District would have to require the following: (a) pennits; (b)
applicants for pennits should demonstrate the impact their project would have on water levels (
before a pennit is granted; and (c) measurement of water-level observation wells in order that the
rate of water-level decline can be monitored. If the rate of water-level decline exceeds the
acceptable rate, then pumping rates may have to be reduced for those large wells regulated by the
District.
The last zone to consider is where the Carrizo aquifer is under artesian conditions. For
practical purposes, this is where the aquifer has 50 or more feet of artesian head above the top of
the aquifer. This portion of the aquifer should be managed so that water levels are not allowed to
fall very far below the top of the aquifer. Management would require pennits, demonstrations by
the applicant, and measurement of water levels in observation wells in order to track declines and
reduce well yields if necessary.
Water Marketing
The District's present rules allow landowners to market up to 2 acre-ftfyr of ground water
per surface acre owned. This is a relatively simple rule to enforce and allows the District to limit
LBG-GUYTON ASSOCIATES
, ~.
- II -
ground-water pumping to the recommended production allowable (12,600 ac-ft/yr). However,
only a limited number of landowners in southeastern Guadalupe County will benefit from the
sale or lease of their water. There are alternatives, which should be considered.
The District could set the production allocation for each acre over the Carrizo-Wilcox
aquifer within the District by dividing the recommended production allowable (12,600 ac-ftlyr)
by the number of acres over the Carrizo-Wilcox in the District. The production allocation per
acre would be small (less than I inch of water per acre per year). However, each landowner over
the Carrizo-Wilcox within the District could participate in the water market ifhe sold or leased
his water right to a "water developer."
Another approach would be to establish the production allocation for each acre based on
the saturated thickness of the Carrizo aquifer in the outcrop and artesian areas. This would
exclude those landowners located over the outcrop of the Wilcox and increase the production
allocation for those landowners located over the Canizo outcrop and artesian areas. In this case,
the production allocation would probably range from less than 1 inch to as much as 3 inches of
ground water per acre depending on location.
The following is expected with regard to the two alternatives: (a) landowners located
( over. the outcrop of the Carrizo-Wilcox aquifer would probably lease or sell their ground-water
(
rights; (b) a maximum of about five or six Carrizo wells would be completed in the favorable
area (southeastern Guadalupe County) if all of the ground-water rights could be obtained from
landowners; and ( c) these alternatives will be more difficult to administer because of the large
number of landowners.
Drought Contingency Planning
There are six steps in preparing a drought contingency plan. The most important
elements from a ground-water hydrology point of view are as follows: (a) assess the District's
vulnerability to drought and define triggering criteria; (b) detennine drought response goals and
measures; and (c) design the plan.
Water-level drawdown measurements in the District that may be used as drought triggers
during drought conditions have not been identified. However, it is recommended that over the
next 5 years rainfall stations and water levels in observation wells be measured in order that
these measurements may be used to revise the initial drought management plan.
LBG-GUYTON ASSOCIATES
- 12 -
It is recommended the initial plan design include tlu'ee trigger levels based on water
demands. The first, second and third levels would begin when daily water demands exceeded 60 (
percent, 70 percent, and 80 percent, respectively, of the District's large-well future development
capacity (10,000 ac-ft/yr, primarily from the Carrizo aquifer).
The recommended response stages are as follows: (a) Trigger Levell - public awareness
and notification of drought conditions; (b) Trigger Level 2 - use of water rate incentives or
penalties (e.g., surcharges for excess use) for water suppliers receiving water from large wells
located within the District; and (c) Trigger Level 3 - water rationing (e.g., water allocation on a
per-household basis) imposed on water suppliers receiving water from large wells located within
the District). Permits for new large wells should incorporate provisions for water rate incentives
and water rationing as described.
( .
LBG-GUYTON ASSOCIATES
(
- 13 -
SELECTED REFERENCES
Ayers, W. B., and A. H. Lewis, 1985, The Wilcox Group and Carrizo Sand (Paleogene) in east
central Texas: depositional systems and deep-basin lignite: University of Texas Bureau of
Economic Geology.
Duffin, G. 1. and G. R. Elder, 1979, Variations in specific yield in the outcrop ofthe Carrizo
Sand in south Texas as estimated by seismic refraction: Texas Department of Water
Resources Report 229.
Hamlin, H. S., 1988, Depositional and ground-water flow systems of the Carrizo-Upper Wilcox,
south Texas: University of Texas Bureau of Economic Geology Report ofInvestigations
175.
( Klemt, W. B., G. 1. Duffin, andG. R. Elder, 1976, Ground-water resources of the Carrizo
(
aquifer in the Winter Garden area of Texas: Texas Water Development Board Report
210, Vol. 1.
Shafer, G. H., 1966, Ground-water resources of Guadalupe County, Texas: Texas Water
Development Board Report 19.
Turner Collie & Braden Inc., 1999, Handbook for drought contingency planning for retail public
water suppliers: workshop handbook prepared for the Texas Natural Resource
Conservation Commission.
LBG-GUYTON ASSOCIATES
TABLEt
PROPOSED WATER-LEVEL OBSERVATION WELLS
Well Reported Latitude Longitude Year Depth of Water- Altitude of Number Owner Completed Well Bearing Land Water Level Remarks
(feet) Unit Surface (feet)
Measuremeut Date from LSD
. (feet) 67-18-603 LemAllen 294150 974548 - 180 Wilcox 405 -18.64 05-26-1970 Unused livestock and
-17.98 01-16-1976 irrigation well. Reported yield of 400 gpm.
67-19-706 Glenwood 293917 974415 1967 357 Wilcox 451 -69.00 07-20-1967 Tested at 150 gpm on Warnicke 7/20/67. Pump set at 289
feet. 67-27-401 New Birth 293251 974345 1961 27 Carrizo 384 -18.50 07-25-1974 Dug welL
Baptist Church
67-27-702 Dusker 293226 974452 1954 462 Carrizo 450 -80.00 12-00-1954 --Harris
67-33-803 J. O. Starcke 292252 975723 -- 140 Carrizo 585 -125.00 08-00-1964 Cased to bottom Reported strong supply.
67-33-901 RH. 292249 975308 1957 1,030 Carrizo 570 -190.80 05-22-1959 Reported yield 1,000 gpm. : Wernert Estate
/~ ~\ .""\
(
(
(
NOTES FROM TWDB GCGCD MANAGEMENT PLAN CHANGES
1. pg 5 10.4 Needs to be clarified as to how many new wells will be evaluated. Want to be able to accomplish the goal
2. pg 6 Methodology for tracking the process is required - suggested text is on the diskette
3. Section 12 pg 6 Need more up to date data - include 1999 data (on diskette)
4.
5.
pg 7 -14
pg 7 15
Delete table 5 & clarify
clarify
6. Have to go thm the orignal process - hearing, GBRA review
7. need to show plan effective for 10 years.
8. pg 5 10.6 add another objective - so that a continuing activity can be seen