TPWD 1960 F-5-R-7 #614: Resurvey and Appraisal of Several Public Waters in Region 3-B
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Report of Fisheries Investigations
ResurveX‘and Appraisal of Several Public waters
in Region 3-3
by
Lawrence-S. Campbell
Project leader
and
James Wilcox
Assistant Project Leader‘
Dingell-Johnson Project F-S-R—T, Job B-22
April 16, .1959 - April 1, 1960
H. D. Dodgen - Executive Secretary
Taxes Game and Fiah_Commiasion
Austin, Taxas
Marion Toole Kanneth C. Jurgena &'William-H. Brown
Coordinator Assistant Coordinators
ABSTRACT
Lakes Trammell, Sweetwater, Abilene, and Fort
Phantom Hill were resurveyed on the Clear Fork of the
Brazos River Watershed. Lakes Brownwood, Scarbrough,
Nasworthy, San Angelo, moss Creek, and J. B. Thomas
were resurveyed on the Colorado River watershed. No
resurvey was done on lakes on the Pecos River but
netting collections were obtained from the river itself.
Altogether, 116 netting and 36 seining collections
were obtained, Although all the lakes resurveyed were
found to have excessive populations of several undesirable
species, the only lakes where management recommendations
were deemed applicable and practical were Lakes Scarbrough
and Sweetwater. The treatment of Lake Scarbrough was
indefinitely postponed as this was the desire of the
municipal officials of Coleman, Texas, who control the
lake. The complete eradication of fish and a restock-
ing program for Lake Sweetwater is scheduled for the
fall of 1960.
Job Completion Report
State of TEXAS
Project No. F—5-B—7 Name: Fisheries Investigations and Surveys of
the Waters of Region 3-B '
JOb No. B~22 Title: Resurvey and Appraisal of Several Pablic
Waters in Region 3aB, Texas -
Period Covered: April 162 1959 — April 1, 1960
OBJECTIVES
A. To study changes in abundance and in the physical condition of the principal
fishery populations within the waters previously surveyed and as may occur.
B. To determine the ecological succession of dominance of various species and to
evaluate the conditions that influence and/or create such trends.
C. To more accurately determine and define the extent and duration of conditions
effecting the dominance and to determine what methods may be employed to bring about
conditions favorable to the propagation and harvesting of game species.
D. To maintain an up-to-date knowledge of the various waters so that reliable
and accurate data will be available in considering future management plans and rec-
ommendations.
PROCEDURE
A total of 116 netting collections and 36 seining collections were obtained from
ten lakes and one river location. All nets used were experimental type nylon gill nets,
measuring 125 feet in length and eight feet in depth. They were made up in five 25-
foot long sections with mesh sizes varying from onewinch square mesh to three-inch
square mesh, increasing in éeinch intervals in each succeeding section. Various
types of seines were employed including a l2wfoot commonsense seine; a 30-foot, fiuinch
mesh, bag seine; a 50~foot, fieinch mesh, straight seine; and a lOO-foot, %-inch mesh,
straight seine.
An attempt was made to Obtain netting and seining samples from the same locations
used previously during the initial survey of the waters involved. When feasible to
do so, data were collected concerning length, weight, sex, and stage of sexual develw
opment either on the complete netting collection Obtained from a location, or on a
representative sample of the individuals collected.
Physical and chemical conditions which mi_ght have a tendency to affect fishery
populations, such as water level and fluctuation, turbidity, temperature, pH, and
dissolved oxygen and carbon dioxide content were noted. Hydrology data was Obtained
on those lakes_where such data has been periodically recorded by the United States
Geological Survey.
FINDINGS '
Clear Fork 2; £32 Brazos River watershed
Lake Trammell - Four netting collections and two_seining collections were Obtained
from this lake. The information gleaned from such limited sampling does not afford a
substantial basis for a comparison of the fishery populations, as they now appear to
be, with the fishery populations as they appeared during the initial inventory. However,
in analyzing the data obtained it appears that black bullhead catfish (Ictalurus melas),
which were the most abundant species in the initial inventory, are now even mere
numerous. Approximately 100 small flathead catfish (Pylodictus olivaris), have been
stocked in this lake since the initial survey was completed in an effert to help control
the vast population of bullheads. These fish have not had time to develop sufficiently
for reproduction or to become large enough to consume a significant number of bullheads.
More and larger largemouth bass (Micropterus salmoides) were obtained in the netting
collections while the number of bluegill sunfish iLepomis macrochirus), collected by
both seine and net decreased considerably. The fact that the resurvey collections
were made in cold weather while most of the initial inventory was done in warm weather
could account for the difference in the size of the samples Obtained of these two
species. However, accepting the samples on their face value, the reason for the change
in abundance of these species is suggested by an ecological relationship that is
known to exist (by analysis of stomach contents). It appears that the largemouth bass
have thinned down the numbers of bluegill sunfish during the fall and winter months
in the absence of the more preferred gizzard shad (Dorosoma cepedianum), which appar-
ently do not occur in Lake Trammell.
In summary then, the results of these resurvey data indicate a favorable trend
as far as largemouth bass and bluegill sunfish are concerned and an unfavorable trend
in regards to bullheads. However, the flathead catfish stocked in the lake may
eventually help remedy the'bullhead prOblem.
No new species were obtained and no new fisheries prOblems were Observed. The
lake is used as a reservoir for municipal water for the City of Sweetwater and water
fluctuations have continued to be fairly common although not extremely abrupt. The
extent that these fluctuations affect the game fish population is not known. No
management effort is recommended for Lake Trammell at this time.
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figure 1. — Results oftgour nets set for the resurvey.of Lake Trammell from April 16, 1959 -
April 1, 19
0
Species Number Percent
Golden shiner
Channel catfish
Largemouth bass
Black bullheads l
Redear sunfish
Bluegill sunfish
White crappie
Total 2
of number
11 20.87
9 n.26
9 b.26
ht 68.25
1 O.h8
2 0.91
2 0.9L
11 100.00
Total weight Average weight Percent Average
lbs. 025. lbs. ozs. of weight "K“
7 8 2.72 17.57 2.13
Channel catfish were released . . . . . . . . . .
29 h 3 1.00 68.52 2.76
5 2 0.57 12.00 2.h8
2 2.00 0.29 3.67
S 2.50 0.7M 3.62
6 3.00 0.88 2.65
M2 11 .. 100.00
....
Figure 2. w A comparison of rough and/or forage species to game species
in four netting collections for the resurvey of Lake
Trammell.
Type of fish Number Percent
of number
Rough and/or forage species
(golden shiners & black bullheads) 188 89.10
Game species
(channel catfish, largemouth bass
and white crappie) 23 10.90
Totals 211 100.00
Lake Sweetwater - Twenty-one netting collections and eight seining collections
were Obtained from this lake. The results of these collections indicate that the
fisheries prOblems in Lake Sweetwater are basically the same as they were during
the inventory period. At the end of the initial inventory it was concluded that,
if the trend towards extreme overdominance by undesirable fish continued, management
work would be necessary. In resurvey data, the percentage of gizzard shad was not
quite as high as in the initial inventory, but that condition can prObably'be
attributed to water and temperature variables which produced different conditions
during the two periods. River carpsucker (Carpiodes carpio), and carp (Cyprinus
carpio), however, were found to have a higher percentage by number in the netting
sample. Since the lake is much lower than it was during the inventory period and
since the City of Sweetwater is willing to fully cooperate in any management effort,
it is recommended that the fish pepulations of this lake and the watershed above be
completely eradicated and restocked with fish from state fish hatcheries. This
recommendation has already been submitted and the JObs have been approved under the
Statewide Rough Fish Control Project, F-lh-D—h. (JOb number 16a-23 and 18a-11).
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Figure h. - A comparison of rough and/or forage species to game species Obtained in.
twenty-one nets set for the resurvey of Lake Sweetwater
Type of fish
Rough and/or forage species
(gizzard shad, river carp-
suckers, carp and black
bullheads)
Game species
(channel catfish, large-
mouth bass, bluegill
sunfish and white
crappie)
Totals
Number
390
23h
62h
Percent
of_number
62.50
37.50
100.00
Total weight Percent
lbs. 028. of weight
188 ll h8.71
198 11 51.29
387 6 100.00
Lake Abilene w Four netting collections and two seining collections were Obtained
from this lake. The outstanding difference in the limited resurvey netting sample
was that river carpsuckers had increased from less than 5 percent of the initial
sample to over 35 percent of the resurvey sample, and that gizzard shad had increased
from less than A percent by number to nearly 11 percent. The average size of white
crappie (Pomoxis annularis) taken in the netting collections had decreased to
slightly over three ounces. The seining sample further substantiated this trend.
No management recommendation is made at this time because the populations of rough
fish have not as yet reached the critical stage, because fishing is still relatively
good in Lake Abilene, and because a high_1evel of water has been maintained in the
lake and management work at this timé would be relatively expensive. However, the
fishery trends, as indicated by the inadequate fish collections made during the re-
survey, are towards dominance by undesirable species and the lake should continue to
be checked periodically as some management work could become necessary in the near
future.
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