TPWD 1958 F-5-R-5 #398: Inventory of Species Present in Lake Fort Phantom Hill near Abilene, Texas: Job Completion Report, Dingell-Johnson Project F-5-R-5, Job B-18
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Report of Fisheries Investigations
Inventory of Species Present in Lake Fort Phantom Hill
near Abilene, Texas
by
Lawrence S. Campbell
Project Leader
Dingell-Johnson Project F-5-R-5, Job B-18
April 16 1956 - April 15, 1958
H. Do Dodgen — Executive Secretary
Texas Game and Fish Commission
Austin, Texas
Marion Toole William H9 Brown
Coordinator Assto Coordinator
JOB COMPLETION REPORT
State of TEXAS
Project N0: F535 Name: Fisheries Investigations and Surveys of the
" waters of Region 3mB:
Jab Noo BulB Title: Inventory of Species Present in Lake Fort
Phantom Hill near Abilene2 Texas
Period Covered: _ April 162 1956 to April 15, 1958
ABSTRACT:
Inventory during the year indicated a numerical dominance by gizzard shad
(Dorosoma cepedianum) and there was evidence of an increase of this population
during the period: Fort Phantom Hill is to be included in reusurvey work for next
year to determine if this species will become a fisheries problem:
'OBJECTIVES:
To determine the species present and their relative abundance as well as to
determine the ecological factors influencing their distribution:
PROCEDURE:
Twenty netting collections were Obtained at ten locations in Lake Fort Phantom
Hill: Experimental nylon gill nets, measuring 125 feet long by 8 feet in depth
and made up in five, 25 foot sections were useda Mesh size of these nets increased
progressively in each following section at onewhalf inch intervals, beginning
with oneminch mesh and terminating with a threeminch mesh section:
Five seining stations were seined twice, once during warm weather and once
during cold weather, for a total of ten seining collectionso Commonsense seines
with oneufourth inch mesh were used for these collections: To estimate relative
abundance a count was made of all individuals taken:
Samples from netting collections were weighed and measured in the fieldo
Stomach contents and sexual maturity were also observed in an effort to Obtain
ecological information.
FINDINGS:
Description w Lake Fort Phantom Hill is located on Elm Creek, twelve miles
northeast of Abilene in Jones Countyo It is one of three water supply lakes for
the City of Abileneo Built in 1938 by the Freeze and Nichols Construction Company
of Fort Herth, this lake has a dam 3,639 feet long with a height of 85 feeto
Besides receiving water from Elm Creek, Fort Phantom Bill also has Cedar Creek,
Little Elm Creek, Deadmanis Creek, Bull Creek and Rainy Creek in its watershed. these creeks
compose a watershed of 38% square miles, There is a pumping station on the Clear
Fork of the Brazos River which supplies the lake with additional water, The
Clear Fork of the Brazos River is only 150 feet away from the shores of Lake Fort
Phantom Hill at this point: The drainage area of the Clear Fork above the pumping
station is approximately 1,500 square mileso
The lake has a capacity of 76,680 acre feet (2% billion gallons) and during
the period covered by this report fluctuated between approximately 60 and 99 percent
full, At maximum capacity it covers an area of 3,950 acres, with a maximum depth
of 65 feet and an average depth of 36 feet:
The water is slightly turbid and also slightly alkaline, having a pH ranging
from 8:2 to 8:60 Most of the inundated area was not cleared of mesquite (Presence
Julifloria) prior to the impoundment of water and the silty sand bottom is covered
with concentrations of the woody plants in various phases of decayo There are
numerous live willows (Salix niger} in the lake arising from the inundated banks
of the creek beds° The lake shore is irregularly shaped: The bottom slopes
gradually to the old stream bed which runs an erratic path through the lakeo No
oxygen deficiencies of excessive dissolved carbon dioxide content were recorded dur-
ing inventory work: Recorded temperatures of the water ranged between 53 and 8%
degrees F,
Netting Results m Tables number 1 and number 2 present the statistical data
obtained from the netting sampleo Twelve species were obtained in the twenty
netting collections made, sap number 1 shows the approximate location of the ten
netting stations where the twenty collections were obtained: Each netting station
was "worked" twice in the course of the survey: However, high winds and rough water
prevented the netting of all ten of these stations at the same time except for the
last visit to the lake when all ten stations were netted:
Io Wartion swim m 0f the twelve different
species shown in table number 1, six were game fish and the other six were rough
specieso "
A, Game species m The two most abundant game species taken were channel
catfish (lctalurus punctatus) and the white bass (Roccus chrysops), Channel catfish
of all sizes were Obtained and it appears that this species has been successful in
producing a good spawn each year, White base were more uniform in site: Most of
the 206 specimens obtained of this species were collected in one netting trip in
early springo The bulk of these were collected in nets set in the deeper cleared
water close to the dam (netting stations l,2, 3, and h as shown on map number 1):
Table number 1 shows the percentage by number and weight and other relative data
'for these two dominant species as well as for the other species collectedo
Only one yellow catfish (P_lodict3§’olivaris3 was obtained from the 80C indie
viduals collected, However, this is not considered to be representative of the
population since good catches of yellow catfish are reported taken from trotlines
during the late spring of each year: ' '
Black bass'(Micropterus salmoides) were not particularly numerous but did
appear to be in excellent condition, Their average "K” factor was 3:13 and their
average weight was two pounds and six ounces: The present high level of the lake
is expected to be a favorable condition for the propagation of this species during
the next few years,
Sunfish and white crappie (Pomoxis annularis) were very small in generalg
White crappic were, however, the fourth most dominant species taken in the netting
sampleo Most of these fish were taken from nets set close to willow trees in
moderately deep water (netting stations 8, 9, and 10 as shown on map number 1).
Bo Rough species m The dominant rough fish species were the gizzard
shad (Dorosoma cepedianumj with 271 specimens” Since this species also appears
to be the dominant forage fish (as determined by stomach analysis of game fish
specimens) it can not be considered detrimental to the condition of the larger
game fish“ It can be considered to be somewhat detrimental, however? to the smaller
fish since it competes with them for food and space and to the angler because it
competes with his lure on the larger game fishess diet°
The river carpsucker (Carpiodes carpio) does not appear to have become the
problem it is in many west Texas lakes but it did compose 6025 percent by number
and 9062-percent by weight of the total netting collectiono
Only one European carp (Cyprinus carpio) was Obtained from the 800 specimens
collected in nets, but this is not considered to be representative as schools of
spawning carp were observed rolling in the shallows during the spring of the yearo
IIo Observations in connection with table number 26 a Table number 2 shows
a comparison by number and by weight between game and rough fish specieso The
netting sample indicates that game fish are slightly dominant over rough species
in number and hold a considerable advantage in weight over the rough species;
discard shad make up the majority of these rough fish as previously discussedo The
h5% by number of rough fish to 55% by number of game fish is not a surprisingly
bad relationship for one of the older West Texas lakeso
Seining Results w the following remarks are considered the best evaluation of
the apparent importance of species taken by coining at five locationso
Gizsard shad (Dorosoma cepedianum) m although these fish are relatively difficult
to capture by coining they were possibly the most numerous of any fish obtained
by that method; however their relatively small size indicated that they were of
potential importance as foodo
River carpsuckcrs (Carpiodes carpio) m numerous in the upper portions of the lake;
however)their importance is not clearly established at this timeo
Carp (Cyprinus carpio)m rare, taken at one location onlyo
Mosquitofish (Gambusia spa) m common and apparently dominate extreme shallow areas
that are protected from wave actiono
Redhorss shiner (figtropis lutrsnsis) a common and widely distributed, the most
numerous Notropis in the reservoira
Parrot minnows (Pimephales spa) m common near the dam and on the cast shorelinsu
The following species were also taken by coining but were not sufficiently numerous
to appear to be of any particular importance from a fishery management point of views
Plains Shiner (Notropis crcobromus), spottail shiner (Notropis venustus), and golden
Shiner (Notemigonus chrysoleucas This last species may have been introduced by
state fish hatcheries or by commercial fishermen as that practice is commono
Game fish taken by seining - Virtually all game fish taken by seining were
either green sunfish (Lepomis cyanellus) or bluegill sunfish (Lepomis macrochirus);
however several largemouth bass fingerling were taken and several white base were
also captured.
SUMMARY AND RECOMMENDATION:
Although the data obtained during the year study at Lake Fort Phantom Hill
is admittedly insufficient for a final appraisal of the fishery problems for that
reservoir the obvious trend toward an extreme population dominance by gizzard shed
is deemed of importance from a future fishery management standpoint» For that
reason it is Considered desirable to discontinue study at this time and include this
reservoir under re-survey work to be done during the next year“ If a natural
contrOl, (as an increase in the white bass population) does not check the trend
it may be recommended that a selective kill may be employed at a future date
to curb the increase Of that species.
\ m
Prepared by: Lawrence S. Campbell Approved by: :ézaflfi M
Project leader Chis. Aquatic Biologist
Date; Au net 7 1958
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