IC 36
GULF TROUGH
GEORGIA STATE DIVISION OF CONSERVATION
DEPARTMENT OF MINES, MINING AND GEOLOGY A. S. FURCRON, Director
THE GEOLOGICAL SURVEY Information Circular 36
HYDRAULICS OF AQUIFERS AT ALAPAHA, COOLIDGE, FITZGERALD, MONTEZUMA, AND THOMASVILLE,
GEORGIA
by Charles W. Sever
Prepared in cooperation with the U.S. Geological Survey, Water Resources Divisio-P
'7'
ATLANTA
1969
CONTENTS
Page
Abstract ____________________ ---------------------------------------------------------------------------------------------------------------------------------------- 3 Introduction -------------------------------------------------------------------------------------------------------------------------------------------------------- 3
Purpose of the Investigations ----------------------------------------------------------------------------------------------------------------- 3 Well-nurnbering Systern --------------------------------------------------------------------------------------------------------------------------- 3 Previous Investigations --------------------------------------------------------------------------------------------------------------------------- 3 AcknowIedgments --------------------------------------------------------------- --------------------------------------------------------------------- 3 Chemical Quality of Ground Water --------------------------------------------------------------------------------------------------------------- 3 Aquifers and Hydraulic Properties --------------------------------------------------------------------------------------------------------------- 5 Methods of Investigations ______________________ ---------------------------- ------------------------------------------------------------------- 5 Hydraulic Properties of the Aquifers -------------------------------------------------------------------------------------------------- 5 Effects of Pumping ------------------------------------------------------------------------------------------------------------------------------- 6 Aquifer Performance Test at Alapaha, Berrien County, Ga._____________________________________________________________________ 6
Hydraulic Properties of the Aquifer ---------------------------------------------------------------------------------------------------- 6 Aquifer Performance Test at Coolidge, Thomas County, Ga-------------------------------------~------------------------------- 6
Current-Meter Test -------------------------------------------------------------------------------------------~------------------------------------ 7 Hydraulic Properties of the Aquifer -------------------------------------------------------------------------------------------------- 11
------------------------------------------~-~~~-~~~-1-1--~-
Chemical Quality of Water ------------------------------------------------ ------------------------------------------------------------------ 11 Aquifer Performance Test at Fitzgerald, Ben Hill County, Ga.------------------------------------------------------------- 11
Current-Meter Test ----------------------------------------------------------------------------------------------------------------------------------- 13 Hydraulic Properties of the Aquifer --------------------------------------------------------------------------------------------------- 13 Effects of Pumping ------------------------------------------------------------------------------------------------------------------------------- 13 Aquifer Performance Test at the Well Field of Southern
Frozen Foods, Inc., Montezuma, Macon County, Ga.------------------------------------------------------------------------ 13 Hydraulic Properties of the Aquifers ------------------------~------------------------------------------------------------------------- 13 Effects of Pumping ------------------------------------------------------------------------------------------------------------------------------- 14 Chemical Quality of Water --------------------------------------------------------------------------------------------------------------------- 14 Aquifer Performance Test at Thomasville, Thomas County, Ga. ------------------------------------------------------------- 14
I
Current-Meter Test --------------------------------------------------------------------------------------------------------------------------------- 15 Effects of Pumping ------------------------------------------------------------------------------------------------------------------------------- 15 Hydraulic Properties of the Aquifer --------------------------------------------------------------------------------------------------- 15 Chemical Quality of Water ------------------------------------------------------------------------------------------------------------------- 16 References ------------------------------------------------------------------------------------------------------------------------------------------------------ 16
ILLUSTRATIONS Page
Figure 1. Location of study areas and geographic coordinates of the wellnumbering system for southwestern Georgia --------------------------------------------------------------------- 4
2. Alapaha well locations ----------------------------------------------------------------------------------------------------------------- 6
3. Geophysical logs of well 20K2 at Alapaha ------------------------------------------------------------------------------- 7
4. Coolidge well locations ------------------------------------------------------------------------------------------------------------- 7
5. Geophysical logs of wells at Coolidge -------------------------------------------------------------------------------------- 10
6. Theoretical water-level decline with respect to distance from a pumped well located at Coolidge, after 10 years continuous pumping at 100 gpm, 1,000 gpm, and 5,000 gpm. --------------------------------------------------------------- 11
7. Fitzgerald well locations ------------------------------------------------------------------------------------------------------------- 11
8. Geophysical logs of well 20M2 at Fitzgerald ------------------------------------------------------------------------ 12
9. Theoretical water-level decline with respect to distance from a pumped well at Fitzgerald, after 10 years continuous pumping ------------------------------------------------------------------------------------------------------------------------------------------- 13
10. Theoretical water-level decline with respect to distance from a pumped well at Southern Frozen Foods, Inc., well field after one day and one year of continuous pumping at 100 gpm and 1,000 gpm ------------------------------------------------------------------------------------------------------------------------- 14
11. Graph showing theoretical water-level decline with respect to distance from a pumped well at Southern Frozen Foods, Inc., well field after 10 years continuous pumping at 500 gpm, 1,000 gpm, 2,000 gpm, and 4,000 gpm ---------------------------------------------------------------------------------- 14
12. Thomasville well locations -------------------------------------------------------------- ____ -------------------------------------- 15
13. Response of the water level in well 14E15 to periodic pumping of wells 14E10, 14E12, and 14E14, Thomasville well field___________________________________________________ 15
TABLES Page
Table 1. Chemical analyses of water --------------------------------------------------------------------------------------------------------- 5
2. Summary of hydraulic coefficients ------------------------------------------------ ------------------------------------------ 6
3. Record of wells ------------------------------------------------------------------------------------ --------------__ -------------------------- 8-9
4. Location and yield of the water-bearing beds in well 20M2 at Fitzgerald --------------------- 13
HYDRAULICS OF AQUIFIERS AT ALAPAHA,
COOLIDGE, FITZGERALD, MONTEZUMA,
AND THOMASVILLE, GEORGIA
Charles W. Sever
ABSTRACT
The results of aquifer performance tests made on four well fields tapping limestones of Miocene, Oligocene, or Eocene age show tha~ the hydrauli.c properties vary greatly from one limestone aqUIfer to another in southwestern Georgia.
Coefficients of transmissibility in the limestones ranged from 120,000 gpd per ft. (gallons per day per foot) at Fitzgerald, Ga., to perhaps as much as 20,000,000 gpd per ft. at Thomasville, Ga. The coefficient of storage ranged from 0.00002 to 0.003.
An aquifer performance test made on sand aquifers of Cretaceous age near ~o:r:t~z_uma, Ga., shows the coefficient of transmissibility to be about 60,000 gpd per ft. and the coefficient of storage to be about 0.002.
The geophysical and lithologic logs and the drawdown versus distance graphs made for the well fields described in this report should enable prediction of the amount of interference between wells and also aid in determining the proper construction and spacing of wells.
Previous Investigations
General information about the hydrogeology and water quality of southwestern Georgia are included in Stephenson and Veatch (1915), Cooke (1943), Wait (1960), and Callahan (1964).
Herrick (1961) has published detailed lithologic and paleontologic logs of numerous wells in
the area, some of which are located within the well fields described in this report.
Results of aquifer performance tests made at other well fields in southwestern Georgia are included in reports by Wait (1963) and Sever (1963, 1965).
Acknowledgments
The author thanks the superintendents of the
water departments of each city described herein
for their cooperation and assistance. Thanks also
are due Mr. John Flatt with Layne Atlantic Com-
pany pany;
Mr. Mr.
JDohanytConarrEwveitrhetJtowhnithCaErrvDerreiltltinDgr~Cllo~mng-
Company, Mr. Rowe with Rowe Brothers Dnllmg
Company, and Mr. Frank Creasy with Creasy
Drilling Company for their assistance in t~sting
the aquifers. The author acknowledges the .mter-
est and assistance of the staff of the Georgia De-
partment of Mines, Mining and Geology, Dr. A. S.
Furcron, Director.
CHEMICAL QUALITY OF GROUND WATER
INTRODUCTION
The mineral content of ground water, though
Purpose of the Investigations
usually higher than that of surface water, does
Ground-water investigations have been ~ade
not vary seasonally. Surface waters may fluctuate appreciably in both mineral content and tern-
at municipal well field~ in Alapaha, .Coohd~e,
perature over a short period of time..The chemi-
--------weFliltz-gfieeralldd-,ofa-nSdouTthhoemrna-sFvriollzeena-nFdooadts,th-eInmc~dMuos~tnteal--
-
cal compositton_i}:f_g:r'QUI!d_w::lt~_var~~--~~~_re-_~ sultof thetype of rock and the length of time the
zuma, Ga. (fig. 1), for the purposes of evaluatu~g
water is in the aquifer. Water from a limestone
the quantity and quality o~ $Tound water ava:Il-
aquifer is usually high in mineral content becau.se
able for industrial and mumcipal use and provid-
of the solubility of the calcium carbonate, while
ing information for the orderly development of this resource. These investiga~ions were ~ade .by
water from a relatively insoluble sand and gravel aquifer may be low in dissolved minerals. Gener-
the U. S. Geological Survey, m. coopera:t1?n With
ally, the farther from the recharge area the water
the Georgia Department of Mmes, Mmmg and Geology, as part of a project ~o evaluate the
is withdrawn from the aquifer, the higher the mineral content.
ground-water resources of Georgia.
Most drinking water standards are based on
those set by the U. S. Public Health Service in
Well-numbering System
The field well-numbering system used in this
report is based upon geographic coordinates. Each
well is assigned two numbers separated by a let-
ter. The first number and the letter refer :to th.e
coordinate system shown on figure 1 and Iden~I
fies the individual 71;2-minute quadrangle m
which the well is located. The final number repre-
sents the well numbered serially within a quad-
rangle. Accordingly, well 18G18 was the 18th well
to be located within the 71;2-minute quadrangle
represented by coordinates 18 and G.
.
Wells for which drill cuttings are available
1962 for water used on common carriers engaged
in interstate commerce (table 1). At the same
time, the American Water Works Association en,.
dorsed these standards and recommended that
they be adopted as minimum criteria for all pub-
lic supplies in the United States.
.
Hardness classification by the U. S. Geological
Survey is related to parts per million (ppm) of
calcium carbonate:
0-60 ppm -------------------------------- soft 61-120 ppm _________________________________moderately hard
121-180 ppm ---------------------------------hard
have been given a Georgia Geological S?rvey (GGS) number. These numbers are shown m ~a ble 3. Drill cuttings from these w~lls are on file in the sample library of the G~orgm Department of Mines, Mining and Geology m Atlanta.
more than 180 ppm _______________________very hard
Chemical analyses of water from wells at Coolidge, Montezuma, and Thomasville are given in table 1.
3
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EXPLANATION
* Location of city where
well field was tested.
10
0
10
20
30MILES
Figure 1. Location of study areas and geog1aphic coordinates of the well-nwmbering syste1n for southwestern
Georgia.
4
Table 1. Chemical analyses of water (Analyses by U. S. Geological Survey unless otherwise shown)
z 0
.......sc
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Parts per million
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Hardness
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-~0tn~:="~
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C/J.~
U. S. Public Health Service
drinking-water standards
0.3
250 250 a1.2 45 500
COOLIDGE
15G7
10-6-64
74 25 0.09 65 31 22 3.5 148 185
15 0.7 0.1 420 288 166 615 8.0 5
SOUTHERN FROZEN FOODS, INC., MONTEZUMA
20M2
8-2-61
75 23 0.06 22 9.0 3.5 0.8 114 0.8 THOMASVILLE
3.0 1.2 0.0 122 92 0 192 7.9 0
14E10 14E10 14E11 t14E12 14E12 14E12 c14E12
2-5-38 12-2-51 12-2-51 1949 3-8-58 12-2-51 8-1-61
71 24 0.02 45 22 7.9 1.0 153 77
71 25 .10 ---- ------
---- 157
71 25
---- 157
---- 18 .1 ---- 31.8
69.6
76 22 .00 47 20 7.8 1.0 158 82
71 26 .07 47 22 6.9 ---- 157 79
72 22 .04 48 21 7.8 1.0 158 78
7.8 0.3 0.1 265 203
7.5
203
418 7.8 ----
7.5
210
425 7.7 ----
11.6
308 187
7.9 ----
9.0 .4 .0 288 200 70 418 7.8 2
7.6 .4 .1 271 208
416
1
8.0 .7 .0 298 206 77 ------ 7.5 25 '
~ Recommended mrunmum concentratwn for area covered by thrs report (average mrunmum daily air temperature of G3.g _
o
o Law and Company, analyst.
70.6 F).
c-Sampled-after-30-days..of-Pur>:LPintg._~~~~~~~~
AQUIFERS AND HYDRAULIC PROPERTIES
Most municipalities and industries located in the Georgia Coastal Plain obtain their water supply from wells that tap water-bearing sedimentary rocks called aquifers. Most of these aquifers are actually aquifer systems, as they are not a single water-bearing bed but generally include several interconnected or related water-bearing beds. Wells that tap limestone aquifers in southwestern Georgia obtain most of their water from a few thin, highly-permeable beds rather than from the entire thickness of the aquifers. Knowledge of the stratigraphic position, thickness, distribution, and yield of these beds, as well as the hydraulic properites of the aquifer system, aid in the proper construction and spacing of wells. In Georgia, the Suwannee Limestone, the Ocala Limestone, and the Lisbon Formation make up the principal artesian aquifer system, the most extensively used aquifer system in south Georgia.
Methods of Investigations
The geologic age of the different rock formations was determined by examining samples of the rocks penetrated by the drilling of water wells.
The tops and bottoms of each formation were lo-
cat~d and t:aced from well to well by comparing
their electr:Ical and gamma-radiation properties.
Water-bearmg zones within the aquifer system
were located by means of a current meter. A cali-
per log was made to determine the inside diameter
of t_he well bore. Th~ hydraulic properties of an
aqmfer were determmed by pumping a well at a
known constant rate and measuring the water-
level c~ange in the pumped well or in nearby ob-
servatiOn wells penetrating the aquifer. 'These
data _are u~ed to solve equations which express the
relatiOnship between the hydraulic properties of
an aquifer and the lowering of water levels near
a pumped well (Theis, 1935 and Ferris and others
1962).
'
Hydraulic Properties of the Aquifers
The principal hydraulic properties influencing the development of an artesian aquifer are the coefficien~s. of transmissib~lity (T) and storage (S). The a?Ihty of an aqmfer to transmit ground water IS expressed by the coefficient of transmissibility, which is defined as the rate of flow of water in gallons per day, through a vertical strip of the aquifer 1 foot wide and extending the fv.ll
5
saturated thickness under a hydraulic gradient of 100 percent (1 foot per foot). The storage properties of an aquifer are expressed by the coefficient of storage, which is defined as the volume of
water released from storage per unit surface area of the aquifer per unit decline in head or water level. Hydraulic properties of the aquifers tested
during these studies are summarized in table 2.
Table 2. Summary of hydraulic coefficients.
Well field
Alapaha Coolidge Fitzgerald Montezuma
(Southern Frozen Foods) Thomasville
Aquifer
Suwanee Limestone do.
Principal artesian aquifer Providence Sand, Cusseta Sand
and Blufftown Formation
Ocala Limestone
Coefficient of transmissibility
(gpd/ft)
240,000 1,300,000
120,000
60,000
20,000,000
Coefficient of storage gals
Not determined 0.00002
.003
.002
Not determined
Effects of Pumping
When a well is pumped, water levels decline in a funnel shape, called a cone of depression, with the greatest drawdown at the pumped well. With continuous pumping, water is taken from storage at greater distances from the pumped well and the cone of depression grows in size and depth until a state of equilibrium is reached. Waterlevel decline is theoTetically directly proportional to the pumping rate and diminishes outward from the pumped well.
In a multiple well system, a cone of depression is formed around each pumped well. When the cones overlap, the wells are said to interfere and water levels decline in a manner directly proportional to the pumping rates and inversely proportional to the logarithm of the distance between wells.
Pumping from wells in artesian aquifers has a widespread effect on water levels. Hydraulic properties detemined for the various well fields described in this report were used to evaluate the magnitude of interference between theoretical wells located within or near the well fields for different pumping rates.
In determining the theoretical drawdown near a pumping well the aquifers tapped were assumed to be insulated from other aquifers by thick impermeable aquicludes. However, water will permeate through most materials if sufficient time and pressure are involved. Most artesian aquifers receive recharge through permeable breaks in the confining aquicludes or by rleakage from the aquiclude itself. Therefore, the predicted drawdowns given for well fields in this report probably are conservative.
AQUIFER PERFORMANCE TEST AT
ALAPAHA, BERRIEN CO., GA.
The city of Alapaha has two municipal wells (20K2 and 20K4). Locations of the two wells are shown on figure 2 and their construction data are summarized in table 3.
During construction of well 20K2, the driller collected samples of the rock penetrated by the well and permitted the author to make electricresistivity and self-potential logs of the upper part of the well before the casing was installed.
400 100 FEET
I
I
20K2
Well and number
Figu?e 2. Alapaha well locations.
After completion, these two types of logs were made of the lower part of the well and a gammaradiation log was made of the entire well. Figure 3 shows these logs and a summary description of the rock samples. The well taps the Suwannee Limestone which is the uppermost member of the principal artesian aquifer system in Berrien County.
Hydraulic Properties of the Aquifer On August 25, 1965, a short aquifer performance test was made by measuring the recovery of the water level in well 20K2 for a half hour after it had been pumped at 41 gpm (gallons per minute) for about 24 hours. The coefficient of transmissibility of the Suwannee Limestone at Alapaha is estimated to be about 240,000 gpd per ft.
AQUIFER PERFORMANCE TEST AT COOLIDGE, THOMAS COUNTY, GA.
Prior to 1902, Coolidge obtained its municipal water supply from two large, shallow dug wells.
6
SELFPOTENTIAL
0 CURVE
MV
--1 25 I-
ELECTRICALRESIST! VI TY
CURVE
GEOLOGY
GAMMA-RADIATION
CURVE
SERIES FORMATION LITHOLOGY
Undifferentiated
Quartz sand
-----~
w
Lt(.) 100
0::: ::J
Cf)
0 z
<[
_j 200
3
0
_j
w
(lJ
Iww
300
LL
z
...
I 368
Ia.-. w 400
0
Seale change OHMS
of 1+---loo--..j casing
Hawthorn
Clayey sand
Formation
w
I
Clay
z w
0 0
~
ji:iI~ Sandy clay Phosphatic sand
~
/ /4..0' IoS~~-~( ~~),CZcJ:::
(5<b
Quartz sand
Quartz sandstone
Tampa Limestone
w
z
w
(.)
Suwannee
0 Limestone
(.9
Sandy limestone
Phosphatic sand
Fossi I i ferous limestone
_j
0 0 - - - - - - - - - - - - -------~-
--- - ---~----
Fig?,ire 3. Geophysical logs of well 20K2 at Alapaha.
~----
In about 1902, the city drilled a 4-inch cased well (15G15) on the northwest side of town and abandoned the two shallow wells. Water from this well began to taste bad and in 1932 the city drilled another well (15G7) and destroyed the old well. In 1962 the pump in well 15G7 broke down and for a
EXPLANATION
15G6
We II and number
C-Tl
r<'l
..15G6
~
\
~
~ J:
(.!)
i
GEORGIA
HIGHWAY
en
WATER TANK~ ~5Gii ::>
i5G7
0
I
188
100 200 300 FEET
I I I
Figure 4. Coolidge well locations.
period of about two months, the city was almost out of water. The city then decided to drill another well. In February, 1964, Rowe Brothers Drilling Co., Tallahassee, Fla., drilled a new well (15Gll) about 65 feet east of well 15G7 (fig. 4). Construction data of these wells are summarized in table 3.
During construction of well 15Gll, electric-resistivity and self-potential logs were made of the upper part of the well before installing the casing; then after completion, these two types of logs were made of the lower part of the well and a gamma-radiation log was made of the entire well. Electric-resistivity, self-potential, gammaradiation, and caliper logs also were made of well15G6.
Samples of the rocks penetrated by well 15G11 were collected by the driller and examined by the author. A summary description of these samples is given on figure 5 together with the logs made of wells 15G6 and 15G11.
Current-Meter Test
On February 5, 1965, water was allowed to flow into well 15Gll through a fire hose at a rate of about 400 gpm while a current meter traversed the well. All the water put into the well apparent-
7
Table 3. Record of wells
Use of water: ES, emergency supply; IS, industrial supply; N, none; OW, observation of water level; PS, public supply Geophysical logs: C, caliper; OM, current meter; ER, electrical-resistivity; SP,* self-potential; GR, gamma-radiation
Well numbers
Field
City GGS
Owner
Driller
Altitude of land Well
Date surface depth drilled (ft) (ft)
Casing
Size From To (in.) (ft) (ft)
Screen Settings Size From To (in.) (ft) (ft
ALAPAHA
20K2 20K4
2
1368 City of Alapaha Dayton Everetts
1965 291 550 8
0 368
none
------
----
1
------
do.
W. R. McGrew 1948 or 49 291 545 8
0 350 ( ?) none
------ ----
COOLIDGE
15G6 ------
15G7
2
15Gll
3
15G15
1
-----------925
----
J. 0. Pilkinton City of Coolidge
do. do.
W. R. McGrew C. C. Renolds Rowe Bros. Unknown
1942 244.6 335 6
1932 252.5 383 6
1963 254.5 385 6
1902 245
?
4
0 212
0 210
0 234
0
?
none none none none
------ ----
------ ----
------ ----
------
----
FITZGERALD
19M1 D or4 355
20M1 B or 2 -------
20M2 A or 1 -----20M3 Cor 3 154
City of Fitzgerald do.
do. do.
Layne-Atlantic
W. R. McGrew
Unknown Layne-Atlantic
1953
1925
1898 1948
?
612 12
0 283
357.8 474 10
0 220
8 198 260
354.6 727 10
0 268
359.3 750 12
0 260
none
none
none none
------
----
------ ----
------
----
------ ----
MONTEZUMA
13S1
1
-------- Southern Frozen Layne-Atlantic
Foods Inc.
13S32
2
--------
do.
do.
--------
------
584 10
0 160
8 160 190
8 210 230
8 235 450
8 465 475
-------- ------ 556 10
0 170
8 170 180
8 190 200
8 210 226
8 231 430
8 440 492
8 497 500
8 510 520
-------8 8 8
---------------
8 8 8 8 8 8
-----190 21
230 23
450 46
------
------
180 19 1
200
21 1
226 23
430 441
492 491
500 511
i
THOMASVILLE
14E10
4
14Ell
3
14E12
5
14E13
6
14E14
2
14E15
1
14E16 ------
56 City of Thomas- Virginia Supply
ville
& Well
186
do.
?
--------
401 ---------------
132
do.
Layne-Atlantic
do.
Merrill Gray
do.
?
do.
?
do.
Layne-Atlantic
1936 262 305
1933 257 550
1949 1950 1917 Prior to 1917 1948
259 399 259 400 257 505 258 548
258 1,635
16
0 112 none
16
0 100 ( ?) none
16
0
95 none
20
0 157 none
12
0 100 none
6
0 ------ none
------ ----- ------ none
------ -----
------ ----
------ -----
------
-----
------
-----
------ -----
------ -----
8
Depth to
water (ft.)
Specific capacity
of well (gpm/ft)
Use of water
216
40
PS
PS
17.9
N
180.4
PS
182.6
PS
?
N
160
64
PS
150
PS
157
PS
161
43
PS
14.5
IS
Geophysical Logs
Water-bearing formations
ALAPAHA
ER, SP, GR
Suwannee Limestone do.
Remarks
COOLIDGE
ER,SP,GR,C ER, SP, GR, CM
Suwannee Limestone do. do. ?
Well abandoned. Well destroyed.
FITZGERALD
ER, SP, GR, C, CM
Suwannee and Ocala Limestone do.
do. Suwannee and Ocala
Limestone, Lisbon Formation.
See Herrick, 1961, p. 20; driller lost circulation at 295 ft.
See Stephenson and Veatch, 1915, p. 141. See Herrick, 1961, p. 17.
MONTEZUMA
Providence Sand do.
Blufftown Formation
------~~----
---~~-
Providence Sand do. do.
Cusseta Sand Blufftown Formation
do.
194
1,000
PS
192
1,060
PS
190
PS
PS
ES
195
ow
N
THOMASVILLE
CR, CM
Suwannee Limestone
Suwannee and Ocala Limestone do. do. do. do.
Several
See Herrick, 1961, p. 400.
Well abandoned and cemented back to an unknown depth. See Herrick, 1961, p. 398.
9
WELL 15G6
WELL 15GII
WELL-
SELF- ELECTRICAL-
GAMMA-
G E Q LOGy
SELF- ELECTRICAL-
GAMMA-
DIAMETER POTENTIAL RESISTIVITY
RADIATION
,
PoTENTIAL RESISTIVITY RADIATION
o CURVE 1
CURVE
CURVE
CURVE
SERIES1FORMATION LITHOLOGY CURVE
Hawthorn Quartz
CURVE
CURVE
o
I
w
Formation sand
u
Sandy
i1
cia
0:::
~
(f) 100
0 z
<{
I I w
2 Chipola Quartz
w Formation sand
-----;100
__J
3:
0
.......
0
w_J 200
en 212
1w-w
lL
z
u
0
I
t-
Sandstone
~
I Tampa Sandy Limestone limestone
:{300
1 s- =-- 13oo
I-
()_
w
0
___WATER-B~ARING ZONE
w z
~ !Suwannee r?ssiliferou
o Limestone l1mestone
400~~::~~~~--~--------~L___
__
__
__
~ijt9
__ _______
l ______ j_~~j_ ______ ~_j ________ j
4 6 8 10 12 DIAMETER, IN INCHES
400
Figure 5. Geophysical logs of wells at Coolidge.
ly flowed into a thin permeable bed between 326 and 328 feet below land surface. Based upon this test, the water-bearing zone in well 15Gll is the upper few feet of the Suwannee Limestone. However, the driller reportedly lost circulation into another permeable bed at 382 feet, but the lowermost 9 feet of this well were presumably plugged
with drill cuttings and the author was unable to test the well from 376 to 385 feet.
Hydraulic Properties of the Aquifer
On February 11 and 12, 1964, an aquifer performance test was made to determine the hydraulic properties of the Suwannee Limestone
0
Q=IOO gpm
I
I
a=Joo gpm
-
2
3
4
1w-~ 5
~
6
:;::
0
~ 7
<[
a:
0 8
v
~
9 10
v ~/ -:P Q =Pumping rate -
~ v ---
-
12
10
_.,/"
I I
I III 100
T =1,300,000
5=0.00002 -
t = 10 years
I I
I I I II
1000
DISTANCE, IN FEET FROM PUMPED WELL
Figure 6. Theoretical water-level decline with respect to
distance from a pumped well located at Coolidge, after 10 years continuous pumping at 100 gpm, 1,000 gpm, and 5,000 gpm. .
aquifer at Coolidge, Ga. During the test, well 15G7 was pumped at a
rate of 165 gpm and the decline in water level was recorded in wells 15G6, 576 feet to the north, and 15Gll, 65 feet to the east. (See fig. 4.) By analyzing the data obtained during this test, using the nonequilibrium formula (Ferris and others, 1962), the coefficient of transmissibility was determined to be about 1,300,000 gpd per ft. The coefficient of storage was determined to be about 0.00002.
Effects of Pumping
The amount of interference in nearby wells by a pumped well, all tapping the Suwannee Limestone at Coolidge, can be estimated using the graph in figure 6. This graph shows the decline of water levels in wells 10 feet to 1,000 feet from a well pumped continuously for 10 years at rates of 100 gpm, 1,000 gpm, or 5,000 gpm. For example, figure 6 shows that pumping a well continuously for 10 years at 5,000 gpm would cause a decline of about 10 feet in a well 100 feet away and about 8 feet in a well 1,000 feet away. With intermittent pumping, the decline should be less than that shown on figure 6.
Chemical Quality of Water
Water pumped from the municipal wells in Coolidge does not exceed the recommended maximum concentration for chemical constituents and is suitable for municipal, irrigation and many industrial uses although it is very hard (288 ppm). Much of its hardness is noncarbonate and is due to dissolved sulfate. A chemical analysis of water from well 15G7 is given in table 1.
AQUIFER PERFORMANCE TEST AT
~~~FITZGERALD;-BEN -HI:&I:rCOUNTY-,GA.
The city of Fitzgerald obtains its water supply from four deep drilled wells, three of which (20M1, 20M2, and 20M3) are located at the water works on Hooker Street (fig. 7). The fourth well (19M1) is located at the corner of Bragg and Ocmulgee Streets. Construction data for these four wells are given in table 3. Samples of the
ACL RR
DO
1000
0
1000 FEET
Figure 7. Fitzgerald well locations.
11
EXPLANATION
20Ml
Well and number
CURRENT- WELL- SELF ELECTRICAL-
METER DIAM POTENTIAL RESISTIVITY
0 TRAVERSE CURVE CURVE
CURVE
GAMMARADIATION
CURVE
GEOLOGY
~ERIES FORMATION LITHOLOGY
100
w 200
(.)
Lt
0::
::>
(j)
266 Bottom
a z
<[
300
_j
~
-
0
_j
w
CD
1ww- 400 r--
lL
z
I"
1-
Cwl... 500 1a
of
cos ina
{_ ~--~--~
-
j+O -50+H 1 M~
<
i
) >
>
~
}
i
:;
Scale Jhonge MV 1+-50->i
Hawthorn
w
z
w
(.)
0
-
Formation
4o~<:'
~~()
~_d- ~ ,~<o~:'.~..0.::~"
vu ci ~ /;; 0 . -<:::-.s. ~
Quartz sand
Sandy cloy
Tampa(?) Lime stone
Sandy limestone
w z
-
w
(.)
Undifferen-
Fossi Iiferous
0
(.9
tiated
I imestone
_j
0
w
z
w
Ocala
Limestone
(.)
Gronulo r fossi Iiferous
limestone
0
600 ~
}
w
r
>
700 ,....
s
,-
-
I I
I
Claiborne Group Sandy limestone
0 I00 200 0 5 I0
REVOLUTIONS DIAMETER, PER MINUTE IN INCHES
FiguTe 8. Geophysical logs of well 20M2 at FitzgeTald.
12
rocks penetrated by wells 19M1 (GGS 355) and 20M3 (GGS 154) were collected by the driller and later examined and described by S. M. Herrick (1961, p. 17-20).
During April, 1965, the pump in well 20M2 was pulled out for repairs. While the pump was out of the well, the author made electric-resistivity, selfpotential, gamma-radiation, caliper, and currentmeter logs of the well. These logs together with a brief summary of Herrick's descriptions of the rock samples are given on figure 8.
Current-Meter Test
On April 6, 1965, water was allowed to flow through two fire hoses at a rate of about 700 gpm into well 20M2 while a current meter traversed the well. Table 4 summarizes the data obtained by this test. Four permeable beds were located between 300 and 720 feet. The most permeable bed was at the contact between the Suwannee and Ocala Limestones at a depth of 339 to 340 feet. This bed is estimated to yield about 45 percent of the water pumped by the municipal wells at Fitzgerald and to be capable of yielding up to 3,000 gpm to a well.
Hydraulic Properties of the Aquifer
From April 1 to April 16, 1965, a water-level recorder was maintained on well 20M2 to record the drawdown and recovery of the water level in response to the intermittent pumping of wells 20M1 and 20M3 located nearby. Pumping of well 20M1 (98 feet away) at a rate of 500 gpm for 8 hours caused a decline in the water level in well 20M1 of about 5 feet. Pumping of well 20M3 (204 feet away) at a rate of 1,000 gpm for 8 hours -~caused a decline_of_about5_feet in well 20Ml.
Analysis of the data obtained onAprTfi2, 1965, "
by using Theis' (1935) nonequilibrium formula shows that the coefficient of transmissibility of the aquifers tapped by these wells is about 120,000 gpd per foot and that the coefficient of storage is about 0.003.
Effects of Pumping
The amount of interference by a pumped well with nearby wells that tap the same limestones as the municipal wells at Fitzgerald can be estimated for long periods of time using the graph in figure 9. This graph shows the decline in water level at distances of 10 feet to 1,000 feet from a well pumped continuously for 10 years at 500 gpm, 1,000 gpm, or 5,000 gpm. For example, figure 9
0
I I I I I 1_1
I I I I II
Q= 500 gprn
10
Q=\000 gpm
20
30
f-
w ~ 40
z
z 50
;;::
0
0
~
60
a:
0 70
80
v90
100 10
/
/
o'~
a~<:o>o~
v 7
Q =Pumping rate
T =120,000 gpd/ft
s =o.oo3
1
t =I 0 years
I I I III
I Ll
I Ill
100
1000
DISTANCE, IN FEET FROM PUMPED WELL
Figure 9. Theoretical water-level decline with respect to distance from a pumped well at Fitzgerald, after 10 years continuous pumping.
shows that a well pumped continuously for 10 years at 1,000 gpm will cause declines about 15 feet in a well located 100 feet away and about 10 feet in a well located 1,000 feet away.
AQUIFER PERFORMANCE TEST AT THE WELL FIELD OF SOUTHERN FROZEN FOODS, INC., MONTEZUMA, MACON COUNTY, GA.
Sou-th-ern-F-rozellFoodS-~ -IllC.~---ObtEdiiSpartm-ffS~-----~
water from two wells, 13S31 and 13S32, located on their property in Montezuma, Ga. and part from the city of Montezuma. The industry reportedly drilled another well during 1965.
Wells 13S31 and 13S32 were drilled by LayneAtlantic Co. in April, 1960, and July, 1962, respectively. Construction data for these wells are summarized in table 3.
Hydraulic Prop,erties of the Aquifers
On April 27 and 28, 1965, an aquifer performance test was made at the Southern Frozen Foods, Inc., well field to determine the hydraulic properties of the sand aquifers tapped by their wells.
During the test, well 13S31 was pumped at 525
Table 4. Location and yield of the water-bearing beds in well 20M2 at Fitzgerald.
Amount of Dep,th to top of
Thickness Estimated total well .yield Estimated maximum yield
casing
permeable bed Altitude of of bed
sup,plied by each bed
of each bedl
(feet)
(feet)
top of bed (feet)
(percent)
(gpm)
300
55
2
20
266
339
16
1
45
632
-277
4
15
718
-363
2
20
1,500 3,000 1,000 1,500
lMaximum yield is based upon a maximum pumping level of 300 feet below land surface.
13
0
o=IIOO lgp~;~l~ iday- . - I
-
'-1-1-
2
Q= 100 gpm; 1= 1veer
4
/
/
6
/,
8
L
10
9;--1:/>.... /
12
~,
0,~
fw~ 14
z
~oo3
- 16
z ~ 18
0
/ ~ 20
a::
0
22
/
//
/
~;;'pe /
~
24
r;;}a/o
26
v
28
30
/ 32 /
/
/
Q=Pumping role
T =60,000 5=0.002 t =Pumping lime
I
34 10
I I
I I II 100
I J
I LI I
1000
DISTANCE, IN FEET FROM PUMPED WELL
Figure 10. Theoretical wate?-level decline with respect to distance from a pumped well at Southern Frozen Foods, Inc., well field after one day and one year of continuous
pumping at 100 gpm and 1,000 gpm.
gpm for an undetermined length of time ; then the pump was stopped at 4:10 p.m. on April 27 and the water-level recovery in well 13S32, located 550 feet to the northeast, was recorded for the next 22 hours.
By analyzing the recovery curve using the modified nonequilibrium formula, the coefficient of transmissibility of the combined Providence Sand, Cusseta Sand, and Blufftown Formation aquifers was determined to be about 60,000 gpd per foot. Their coefficient of storage was determined to be about 0.002.
Effects of Pumping
The amount of interference by a pumped well with nearby wells in the Southern Frozen Foods, Inc., well field can be estimated using the graph in figure 10. This graph shows the decline in water level at distances of 10 feet to 1,000 feet from a well pumped continuously for one day and one year at pumping rates of both 100 gpm and 1,000 gpm. For example, pumping a well at 1,000 gpm for one day will cause a decline of 7 feet in the water level of a well 500 feet away. With continued pumping, the decline increases and after one year the water level in a well 500 feet away will have declined about 18 feet. With intermittent pumping, the decline should be less than that shown on figure 10.
The amount of interference by wells in the Southern Frozen Foods, Inc., well field with municipal or other wells located in the area can be
6
I I I I I II
- .. I I
. .. I III
Q=500 gpm
10
Q=IOJO~
-- 20 ~ ~1---
30
:...---~
------ --- 40
-'2.00~ ~
--------- fw-
w
50 ______..,'-""'
LL.
z 60
2
~ 70
0
;;:: ~ 80
/
~0eJo; P
v /
/
0
Q =Pumping role
90
/
100
v
T =60,000
s =0.002
t = 10 years
v /
110
120
130 100
II I
J l
I I II
1000
10,000
DISTANCE, IN FEET FROM PUMPED WELL
Figure 11. Graph showing theoretical water-level decline with respect to distance from a pumped well at Southern Frozen Foods, Inc., well field after 10 years continuous
pumping at 500 gpm, 1,000 gpm, 2,000 gpm, and 4,000 gpm.
estimated using the graph in figure 11. This graph shows the water-level decline in wells 100 to 10,000 feet from a well continuously pumped at 500 gpm, 1,000 gpm, 2,000 gpm, and 4,000 gpm, for a period of 10 years. For example, figure 11 shows that continuous pumping for 10 years at a rate of 1,000 gpm in a well at Southern Frozen Foods, Inc., would cause a water-level decline of about 14 feet in a well 5,000 feet away. However, with intermittent or seasonal pumping the decline should be less than that shown on figure 11.
Chemical Quality of Water
Water pumped from the industrial wells at Southern Frozen Foods, Inc., is moderately hard (92 ppm) and of good chemical quality. It does not exceed the recommended maximum concentration for chemical constituents and would be suitable for municipal, irrigation, and many industrial uses. However, its fluoride (1.2 ppm) content is at the recommended maximum concentration for consumption. A chemical analysis of water from well 20M2 is given in table 1.
AQUIFER PERFORMANCE TEST AT
THOMASVILLE, THOMAS COUNTY, GA.
The city of Thomasville obtains its water from 5 wells spaced 70 to 700 feet apart (fig. 12) that tap the Ocala Limestone. A continuous record of changes in water level caused by pumping of these 5 wells is being obtained from a sixth well (14E15) located within the well field. Construction data for all of the wells at the Thomasville well field are given in table 3.
14
Sampies of the rocks penetrated. by weils 14E16 (GGS 56), 14E11 (GGS 186), 14E13 (GGS 401), and 14E16 (GGS 132) were collected by the driller and later examined and described by Herrick (1961, p. 398-401) and Applin and Applin (1964, p. 212-216). A geologic summary of well 14E16 (GGS 132), a 1,635 foot deep exploratory well, follows:
.14EI3
Figure 12. Tho'Y!~asville well locations.
Current-Meter Test On February 4, 1964, water was injected through two fire hoses at a rate of about 760 gpm into well 14E15 while a current meter traversed the well. All of the water appeared to flow into a 7-foot-thick permeable bed in the Ocala Limestone at a depth of 420 to 427 feet below land surface. No additional permeable beds were found in the well.
Effects of Pumping During Decemb,er, 1963, a water-level recorder was installed on well 14E15 and a record was kept of the time each pump in the municipal well field was started or stopped. Figure 13, a copy of the recorder graph of well 14E15 for December 26 to 30, 1963, shows how the water level changed in response to pumping from three of the Thomasville wells. The water level generally oscillated up and down with diminishing amplitude for about 2 minutes after a pump was started
14E12
0 z
<! ..J
~ 195.0 r-----+--1.---+--Po:=f-+-+-+--+-+----1
..J
,~..
uww.
~ 195.1 r - - - - - + - - - - + - - - - + - - ' - - - - " 1 - - - - 1
_j
w w >
..J
!w";;'
ll: 195.2 ' - - 2 6_ __,__ _2_7- - ' - - 2 - 8_ ___,___ _2_9--'----3-0----'
DECEMBER, 1963
Figure 13. Response of the water level in well 14E15 to periodic pumping of wells 14E10, 14E12, and 14E14, Thomasville well field.
or stopped. The amount and direction of this oscillation and also the change in the watel level depended upon whether the pump was started or stopped, the pumping rate, and the distance from the observation well to the pumped well. Well 14E12 is located about 310 feet west of the observation well and was pumped at a rate of 1,170 gpm. Well 14E10 is located about 310 feet to the southwest and was pumped at a rate of 1,000 gpm. Well 14E14 is located about 95 feet to the southwest and was pumped at a rate of 500 gpm.
Hydraulic Prop,erties of the Aquifer
Tli:e-lack~of~aevelopment_of_a-drawdown~cone---
around the Thomasville well field after prolonged pumpage indicates that the aquifer tapped by the Thomasville wells is extremely permeable. This permeability probably results in part from ground-water solution of the limestone along numerous joints created during folding and faulting of the rocks in the Thomasville area (Sever, 1966).
Aquifer performance tests were made at the Thomasville well field by recording the drawdown of water levels in well 14E15 caused by pumping other municipal wells at rates o 500 gpm to 3,200
Geologic Age
Pliocene to Recent (undifferentiated)
Miocene (undifferentiated)
Oligocene (undifferentiated)
upper Eocene (Ocala Limestone)
middle Eocene (Lisbon Formation)
middle Eocene (Tallahatta Formation)
Geologic summary of well 14El6
Lithology
Thickness (feet)
Clayey sand
35
Sand and sandy
135
limestone
Fossiliferous
130
limestone
Dolomitic limestone
725
Glauconitic limestone
587
Glauconitic sand
23
Depth (feet)
35 170 300 1,025 1,612 1,635
15
gpm. Close spacing of wells, oscillation of water levels after each pump was started or stopped, intermittent pumping of nearby wells, and the short time interval between pumping cycles of municipal wells make the data obtained from the aquifer performance tests difficult to interpret. However, analyses of these data suggest that the coefficient o;f transmissibility of the principal
artesian aquifer system at Thomasville is ex-
tremely large-possibly as large as 20 million
gpd per foot. The coefficient of storage is small-
probably less than 0.00001.
Chetnical Quality of Water
Water from the municipal wells in Thomasville is very hard (187-210 ppm) but contains mineral concentrations that are well below the recommended limits for drinking water. The concentrations of dissolved minerals from three of the municipal wells are summarized in table 1.
Thomasville has recently built a modern watersoftening plant but chemical analyses of the treated water are not presently available. However, the treated water should be much softer and lower in dissolved solids.
REFERENCES
Applin, E. R. and Applin, P. L., 1964, Logs of selected wells in the Coastal Plains of Georgia: Georgia Geol. Survey Bull. 74, 229 p.
Callahan, J. T., 1964, The yield of sedimentary aquifers of the. Coastal Plain, Southeast River Basins: U. S. Geol. Survey Water-Supply Paper 1669-W, 56 p.
Cooke, C. W., 1943, Geology of the Coastal Plain of Georgia: U. S. Geol. Survey Bull. 941, 121 p.
Cooper, H. H., Jr., and Jacob, C. E., 1946, A generalized graphical method of evaluating constants and summarizing well field history: Am. Geophys. Union Trans., v. 27, no. 4, p. 526-534.
Ferris, J. G., Knowles, D. B., Brown, R. H., and Stallman, R. W., 1962, Theory of aquifer tests: U. S. Geol. Survey Water-Supply Paper 1536-E, 174 p.
Herrick, S. M., 1961, Well logs of the Coastal Plain of Georgia: Georgia Geol. Survey Bull. 70, 462 p.
Lang, S. M., 1961, Methods for determining the proper spacing of wells in artesian aquifers: U. S. Geol. Survey Water-Supply Paper 1545-B, 16 p.
Sever, C. W., 1963, Ground-water resources of Bainbridge Air Base, Decatur County, Georgia: Georgia Geol. Survey Min. Newsletter, v. 16, nos. 1 and 2, p. 39-43.
---1965, Ground-water resources of Bainbridge, Ga.: Georgia Geol. Survey Inf. Circ. 32, 10 p.
---1966, Miocene structural movements in Thomas County, Ga.: U. S. Geol. Survey Prof. Paper 550-C, p. C12-C16.
Stephenson, L. W., and Veatch, J. 0., 1915, Underground waters of the Coastal Plain of Georgia: U. S. Geol. Survey Water-Supply Paper 341, 539 p.
Theis, C. V., 1935, The relation between the lowering of the piezometric surface and the rate and duration of discharge of a well using ground-water storage: Am. Geophys. Union Trans., v. 16, p. 519-524.
----1963, Spacing of wells in shortcuts and special problems in aquifer tests: U. S. Geol. Survey WaterSupply Paper 1545-C, p. 113-115.
U. S. Public Health Service, 1962, Drinking water standards: U. S. Public Health Service Pub. 962.
Wait, R. L., 1960, Source and quality of ground water in southwestern Georgia: Georgia Geol. Survey Inf. Circ. 18.
----1963, Geology and ground-water resources of Dougherty County, Ga.: U. S. Geol. Survey WaterSupply Paper 1539-P, 102 p.
16