TPWD 1974 F-5-R-21 #1592: Region I-B Fisheries Studies: Fisheries Management Recommendations, Federal Aid Project No. F-5-R-21
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PERFORMANCE REPORT
As required by
FEDERAL AID IN FISHERIES RESTORATION ACT
TEXAS
Federal Aid Project No. F-5-R-21
REGION I-B FISHERIES STUDIES
Objective 13: Fisheries Management Recommendations
Project Leader: Billy J. Follis
Clayton T. Garrison
Executive Director
Texas Parks and Wildlife Department
Austin, Texas
Lonnie J. Peters Robert J. Kemp, Director
Chief, Inland Fisheries Fisheries Division
March 24 lo74
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Summary
The objective of this study is to recommend management practices for the public
waters of Region I-B.
Fisheries surveys were conducted on 16 public lakes and two public streams in
Region I-B to determine and recommend management practices. These surveys
included fish sampling with gill nets and seines; collection of physical,
hydrological and ecological data; aquatic vegetation checks, and water analysis.
Preliminary meetings and public hearings were attended for the Permian Basin
and Edwards Plateau Regulatory Districts. The existing fishing regulations
were considered adequate for the existing fisheries resources and no changes
were necessary.
Supplementary hatchery stocking was the most common management activity
recommended during this segment. Fifteen public lakes and six public streams
received a total of 4,710,000 fry and 1,365,333 fingerlings of seven game
fish species. The majority of these fish were supplied by the two San Angelo
State Hatcheries.
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State:
PERFORMANCE REPORT
Texas Project Number: F+5=R=21
Project Title: Region I-38 Fisheries Studies
. 5 : pecersmner
Project Section: Inventory _— ee
Study Title: Fisheries Management Recommendations _ 7
Contract Period: . From March 1, 1973 To February 28, 1974
Program Narrative Objective No.: 13
PS Objectives:
Il.
T
MW PON re
o determine the need for in Region I-B waters,
- Changes in fish harvest regulations
Population control
Stocking
Vegetation control
. Updating public access information.
Segment Objectives:
One through five above.
Summary of Progress: Proposed fishing regulations were discussed with
concerned Department personnel at preliminary meetings in the Edwards
Plateau and Permian Basin Regulatory Districts. Current fisheries sur-
vey data, existing fisheries regulations, and applicable developments
in fisheries management elsewhere provided the basis for proposed fish
harvest regulations. The resulting proposals were presented at public
hearings in each county under regulatory authority.
Fish populations were sampled with standard gill nets and seines. The
standard gill net used is 150 feet long and 8 feet deep with mesh sizes
varying from i to 3% square inches. Additional large mesh (3- and
3%-square-inch-mesh) gill nets were used to more adequately sample
fishes of larger sizes.
The number of nets set was determined by the size of the impoundment,
water conditions and time of year. The size of seines used is given
with each survey results table.
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All fish collected in gill nets were counted and weighed. A sample
of fish, usually up to 15 of each game species, was measured and
examined for sexual development and stomach content. Total numbers,
total weights, percentage composition, average weights and condition
factors ("K") were tabulated. Fish taken in seines were counted and
length ranges were recorded. Several specimens of each species were
preserved in formalin and returned to the laboratory where identifi-
cations were confirmed.
Vegetation observations were made during each survey and records were
made as to the kind and abundance. This information will be dis-
cussed only when significant.
Air and water temperatures, hydrological data, turbidity, weather
conditions and other physical data were recorded in each survey.
Water analyses, including dissolved oxygen, carbon dioxide, alkali-
nity, total hardness, chlorides and pH were conducted on most waters.
This type of information will be discussed in this report only when
pertinent.
Data for each body of water were examined to determine which waters
would be considered for population control measures. The criteria
for considering management efforts were population of undesirable
species in excess of 80 per cent by weight and/or number, lake capaci-
ties, water usage, and the "cost-benefit ratio" of a treatment.
Several public waters surveyed during this segment were recommended
for supplementary hatchery stocking of fingerling game fish for one
or more of the following reasons: (1) the degree and survival of game
fish reproduction, (2) reservoir capacities, (3) food abundance,
(4) fishing pressure and (5) past production records.
III. Significant Deviation: No significant deviation from planned acti-
vities were encountered. All public lakes of Region I-B were sur-
veyed during this segment with the exception of two minor lakes that
were extremely low.
No major improvements or developments of access and/or facilities were
found, therefore, updating of the Statewide Public Access Bulletin was
not necessary.
IV. Conclusions, Evaluations and Recommendations: The existing fish harvest
regulations for Region I-B were found to be satisfactory for the pre-
sent resources and no changes were proposed or adopted.
The public waters of Region I-B surveyed during this segment are listed
in Table 1. A comparison of the average coefficients of condition
("K" factors) for all game species collected with gill nets at all
waters surveyed is presented in Table 2. The 1973 supplementary hatchery
stocking of game fish is found in Table 3.
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Table l.
Name
Amistad Reservoir
Ascarate Lake
Balmorhea Reservoir
Diablo I Lake
Elm Creek Lake
E. V. Spence Reservoir
Macho Lake
Mountain Creek Lake
Nasworthy Lake
North Concho Reservoir
Oak Creek Reservoir
Red Bluff Reservoir
Robert Lee City Lakes
Twin Buttes Reservoir
Valley Creek Lake
Winters Lake
Colorado River
San Saba River
County
Val Verde
El Paso
Reeves
Hudspeth
Runnels
Coke
Hudspeth
Coke
Tom Green
Tom Green
Coke
Reeves
Coke
Tom Green
Runnels
Runnels
Concho
Menard
Waters Surveyed During Segment 21
Surface Acres
Size
64,900
50
573
84
55
14,950
40
95
1,596
5,440
2,375
11,700
15
9,080
250
Number of
Visits
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-7-
The evaluation, discussion, and recommendations for Objectives 2,
3, and 4 will be combined and reported separately for each con-
cerned body of water for expediency. Stocking requests for 1974
have been made but undoubtedly will require several changes because
of unpredictable water levels in West Texas.
Lake Amistad
The results of two surveys on Amistad (May and November 1973) are
combined in Table 4. The fish population appears stable in all
respects, with most species near their long-term averages in netting
results for the past three years. The average weight of smallmouth
buffalo continues to increase, however, despite the use of the same
types of nets since 1968.
The International Boundary and Water Commission and Texas Water Rights
Commission have cooperated with the Texas Parks and Wildlife Depart-
ment each spring in stabilizing the water level during the largemouth
bass spawning season (February through April). By allowing undisturbed
spawning and encouraging high fry survival, this practice has apparently
succeeded in maintaining a substantial crop of harvestable largemouth
bass from year to year without supplementary stocking. Age class 0
and 1 fish were common in this segment's surveys.
Lake Amistad has been selected as a potential candidate for striped
bass stocking. The great areas of open water, largely unutilized now,
could possibly contribute to an open-water predator fishery. However,
before any new species are introduced into Amistad, harvest and standing
crop data should be gathered intensively for at least one year as base-
line data from which the effects of stocking can later be measured.
Recent informal discussions with Mexican officials indicate that
cooperative studies and management programs involving fisheries
workers of both countries are promising possibilities. This is con-
sidered as an important opportunity and should be officially encour-
aged.
Ascarate and Ascarate Fisherman's Lakes
Results of the single survey of these lakes, made in October 1973, are
combined in Table 5 because the two lakes are connected by a short con-
duit through which water flows from Ascarate to the smaller lake. Both
lakes produce few game fish because of heavy fishing pressure and skiing
and boating on the larger lake. The populations of carp and gizzard
shad are too large, although carp are often sought and utilized by
local fishermen.
Threadfin shad were introduced in 1971. Subsequent surveys produced
no survivors and the effort was regarded as a failure. However, in
October 1973, six threadfins were seined from the smaller lake Fisher-
man's). Further surveys will determine if their population will grow
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Table 4. Survey Results Amistad Reservoir, May 22, 23, 24, 1973 and
November 6, 7, 8, 1973. Results of fifty-nine standard gill
nets and twenty-one large-mesh nets.
Per Cent Total Wt. Avg. Wt. Per Cent Average
Species Number By No. Pounds Pounds By Wt. "K"
Spotted gar 3 .18 3.52 1.17 13
Longnose gar 39 2.43 84 .62 2.16 332
Gizzard shad 457 28 .48 204 .34 44 8.01
Carp 74 4.61 126.84 1.71 4.97
River carpsucker 83 5 «LZ 132 .44 1.59 3«19
Smallmouth buffalo 535 33 .33 1433 .00 2.67 56.16
Gray redhorse 9 56 11.53 1.28 45
Blue catfish * 12 75 15.81 1.21 .62 1.54
Black bullhead 1 .06 «25 .25 .O1
Channel catfish * 48 2.99 63 .50 1.32 2.49 1.65
Flathead catfish * 46 2.87 303 .22 6.59 11.89 1.97
White bass * 47 2.93 42.78 91 1.67 2.46
Warmouth * 6 .37 1.57 .26 .06 3.30
Redbreast sunfish * 5 31 49 .09 .02 3.36
Green sunfish * 2 13 -26 13 -O1 3.55
Bluegill * 101 6.29 12.20 12 48 3.62
Longear sunfish * 1 .06 .09 -09 OL 3.64
Redear sunfish * 3 18 54 .18 .02 3.67
Largemouth bass * 58 3.62 48 .07 .82 1.88 2.29
White crappie * 39 2.43 22.66 -58 .89 2.54
Black crappie * 1 .06 .80 .80 .03 2.65
Freshwater drum 35 2.19 42.98 1.22 1.69
Total 1605 100.00 2551.51 100.00
Game Fish * 369 22.99 511.99 20.07
Rough Fish 1236 77.01 2039 .52 79.93
Seining results Amistad Reservoir (Bag 26' x 6' x 4-inch-mesh
seine, and 20' x 6' x 1/8-inch-mesh seine).
Species Number Size Range In Inches .
Golden shiner 1 1-24
Blacktail shiner 65 1-4
Fathead minnow 4 1-2
Bullhead minnow 6 14-2
Mosquitofish 5 3-1
Redbreast sunfish 2 3/4-34
Bluegill 7 2-4
Largemouth bass 2 3-3% ee
Ne)
he
Total
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Table 5. Survey results Ascarate Lake, October 3, 1973.
Results of four standard gill nets and one large-mesh net.
Per Cent Total Wt. Avg. Wt. Per Cent Average
Species Number By No. Pounds Pounds By Wt. Nie
Gizzard shad 31 30.39 21.00 .67 17.90
Carp 20 19.60 68 .00 3.40 57.99
River carpsucker 3 2.95 4.57 1.52 3.90
Black bullhead 12 11.76 1.98 .16 1.69
Channel catfish * 25 24.51 20 .37 81 17 .37 1.70
Bluegill * 7 6.86 49 .07 42 3.55
White crappie * 1 -98 42 -42 .36 2.62
Black crappie * 3 2.<95 43 14 231 2.89
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Total 102 100 .00 117.26 100 .00
Game Fish * 36 35.30 21.71 18.52
Rough Fish 66 64.70 95.55 81.48
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Seining results Ascarate Lake (Bag 26' x 6' x %,-inch-mesh
seine, and 20' x 6' x 1/8-inch-mesh seine).
—_—_—_ ee
Species Number Size Range In inches __
Gizzard shad 100 2-6
Threadfin shad 6 3-4
Carp 1 10
Golden shiner 66 15-6
Red shiner 25 1-14
Bullhead minnow 6 14
Black bullhead 1 8
Green sunfish 2 3
Bluegill 70 1-4
Longear sunfish 2 2-3
Black crappie 6 6-7
Largemouth bass 14 2-8
Seca nEEnnennnreneeeeeeee
Total 299
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Jl.
partially displace gizzard shad as hoped, and provide more available
forage for game fish.
Because of intensive fishing pressure and poor conditions for adequate
game fish reproduction, stocking of sub-adult channel catfish and
largemouth bass has been done annually for several for several years.
This practice should be suspended for a year or more to check recruitment.
Lake Balmorhea
Fifty-seven flathead catfish were stocked in Lake Balmorhea in 1970
to reduce the stunted population of small sunfish. The most recent
survey, conducted in September 1973, (Table 6) shows no evidence of
either flathead reproduction or a reduction of small sunfish. How-
ever, the catfish have survived and are harvested from time to time,
and there is no reason to believe that they will not reproduce here.
Lake concessionaires report that Lake Balmorhea continues to yield a
satisfactory game fish harvest and is a popular fishing lake in West
Texas. It has an abundant and varied supply of small forage fish and
should be considered for introduction of an open-water predator species
such as white bass, striped bass, or walleye.
Lake Diablo I
According to an October 1973 survey (Table 7), crappie in Lake Diablo I
are overpopulated and undersized as in past surveys. A management
technique which has been shown effective in other applications, intro-
duction of a new large predator species, was tried here in December
1973. Twenty-seven adult and sub-adult flathead catfish were collected
from other regional lakes and transported to Lake Diablo I. Further
surveys will be made to evaluate the success of this action and to
determine other management needs.
Despite the overabundant crappie and large carp, this lake regularly
produces large game fish. A largemouth bass weighing more than 12
pounds was captured in May. This fish was not caught on a hook but
jumped into the boat in pursuit of a lure which the fisherman had just
retrieved from the water.
Elm Creek Lake
This old impoundment serves very little as a fishery. Sedimentation
has reduced its depth and almost destroyed all game fish spawning
habitat. Supplementary hatchery stocking has produced little improve-
ment. Only three desirable species were collected with gill nets and
accounted for 12% by number and less that 4% by weight of this year's
sample (Table 8).
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Table 6.
-ll-
Survey results Balmorhea Lake, September 11, 12, 1973.
Results of six standard gill nets and four large-mesh (cis
Per Cent
Total Wt.
Ave. Wt.
Per Cent Average
Species Number By No. Pounds Pounds By We. UK"
Carp 107 22.62 341.00 3.18 72.41
Golden shiner 11 2.32 1.84 -16 .39
River carpsucker 4 #85 20.00 5.00 4.24
Channel catfish * 37 7.82 38.99 1.05 8.28 1.4
Flathead catfish * 2 42 31.60 15.80 6.71 2.06
Bluegill *« 222 46.94 16.85 .07 3.58 3.03
Redear sunfish * 2 42 41 .20 .09 3.40
Largemouth bass * 14 2.96 12.78 -91 2.71 2345
White crappie * 51 10.78 5.24 -10 1.12 2.17
Black crappie * 23 4.87 2.21 -09 47 2.48
eee _
Total 473 100 .00 470 .92 100 .00
Game Fish * 351 74.21 108 .08 22.96
Rough Fish 122 25.79 362 .84 77.04
Seining results Balmorhea Lake, (Bag 26' x 6' x ¥-inch-
mesh seine, and 20' x 6' x 1/8-inch-mesh seine).
eee
Species Number Size Range in Inches _
Mexican tetra
Carp
Golden shiner
Fathead minnow
Variegated cyprinodon
Mosquitofish
Warmouth
Green sunfish
Orangespotted sunfish
Bluegill
Largemouth bass
White crappie
Black crappie
Tidewater silversides
bo
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Total 1693
neem
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7
Table 7, Survey results Diablo I Lake, October 4, 1973.
Results of two standard gill nets, and 1 large-mesh nets.
Per Cent Total Wt. Avg. Wt. Per Cent Average
Species Number By No. Pounds Pounds By Wt. Wii
Carp 12 10.25 46.00 3.83 77 14
Channel catfish * 3 2 DL 5.08 1.69 8.52 1.51
Bluegill * 10 8.54 75 .07 1.25 3.79
White crappie * 92 78.64 7.80 -08 13.09 2wld
Total 117 100.00 59.63 100 .00
Game Fish * 105 89.75 13.63 22 .86
Rough Fish 12 10.25 46 .00 77.14
Seining results Diablo I Lake, (Bag 26' x 6' x 4-inch-mesh
seine, and 20' x 6' x 1/8-inch-mesh seine).
Species Number Size Range in Inches
Golden shiner 57 yn
Mosquitofish 12 1-1%
Green sunfish 1 1
Orangespotted sunfish 1 1
Bluegill 175 1-4
Largemouth bass 15 23-5
White crappie 156 1-24
Logperch 2 3-34
Total 419
nn A
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-13-
Table 8. Survey results Elm Creek Lake, June 6, 1973.
Results of three standard gill nets, and one large-mesh net.
Per Cent Total Wt. Ave. Wt. Per Cent Average
Species Number By No. Pounds Pounds By Wt. mi
Longnose gar 1 .63 6.49 6.49 4.39
Gizzard shad 84 53.16 20.53 .24 13.88
Carp 9 5.70 38.00 oe ele 25.71
River carpsucker 12 7.59 13.00 1.08 8.80
Smallmouth buffalo 19 12.02 52 .00 2.73 35.17
Black bullhead 7 4.44 2.24 «32 1.52
Channel catfish * 4 2«53 4.00 1.00 2.70 1.56
Warmouth * 1 .63 .09 -09 -07 3.82
White crappie * 14 8.86 1.47 -10 99 2.73
Freshwater drum 7 4.44 10.00 1.42 6.77
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Total 158 100 .00 147 .82 100 .00
Game Fish * 19 12.02 5.56 3.76
Rough Fish 139 87.98 142 .26 92.24
in enneeeeee
Seining results Elm Creek Lake, (Bag 26' x 6' x k-inch-mesh
seine, and 20' x 6' x 1/8-inch-mesh seine).
eee
Species Number Size Range in Inches
eee
Gizzard shad 6 3-6
Red shiner 120 4-14
Bullhead minnow 4 1-2
River carpsucker 5 4
Mosquitofish 50 4
Green sunfish 1 2
Orangespotted sunfish 3 1-2
Bluegill 2 2
Largemouth bass 21 45-2
Total 212
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~1h~
E. V. Spence Reservoir
Since its completion in 1969, this 15,000-acre reservoir has im-
pounded only about one-third of its capacity. The water level fluctu-
ates as the Colorado River Municipal Water District makes withdrawals
for municipal use by the cities of Odessa, Midland, Big Spring,
Snyder and San Angelo.
Standard survey results for the July collection at E. V. Spence
(Table 9) reflect the beginning of a stabilization of the fish popu-
lation. The species composition by per cent number and weight is very
similar to last segment's collection. However, largemouth bass were
not collected by either nets or seines and this might be considered as
a significant factor if it reoccurs next segment.
The experimentally introduced striped bass have become a significant
part of this West Texas fishery. Creel surveys, conducted under Job
16 of this project, show that 10% of the fishermen are seeking this
large open water predator. A striper evaluation collection (Project
F-27-R, Job 6) conducted during cooler months captured 142 striped bass
which accounted for 33.09% weight of all fish caught (Table 10). Two
stripers weighing more than 14 pounds were taken by fishermen in
January 1974.
Gizzard shad, threadfin shad, and tidewater silversides are abundant
and provide ample forage for all predator species.
The annual stocking of striped bass fingerlings should be continued
since this reservoir is supplying brood fish for the statewide striper
program.
Lake Macho
The harvest of channel catfish in Lake Macho is believed to be main-
tained by annual supplementary stocking. The 1973 stocking of hatchery-
reared catfish was evident in the October 1973 survey (Table 11).
On the other hand largemouth bass are missing from this survey. This
may be due in part to the scarcity of hatchery-reared bass for the past
two years; however, past surveys of Macho have characteristically col-
lected only a few large bass. Further surveys will be necessary to
determine if their population is declining and whether supplementary
bass stocking is necessary.
As before, the carp in Macho appear to be few but large. Carp smaller
than 5 pounds are rarely netted here. Bluegill are numerous and stunted
as in most other small West Texas lakes. Despite these factors, the
game fish harvest from this small but popular lake is reported by the
concessionaire to be satisfactory.
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15+
Table 9. Survey results E. V. Spence Reservoir, July 4, 5, 1973.
Results of eleven standrad gill nets, and six large-mesh nets.
Per Cent Total Wt. Avg. Wt. Per Cent Average
eee
Species Number By No. Pounds Pounds By Wt. NR
Longnose gar 27 5.03 74.00 2.74 15.75
Gizzard shad 178 33.21 25.00 .14 5.32
Carp 48 8.96 40.00 .83 8.52
River carpsucker 61 LL.38 76.00 1.24 16.18
Blue catfish * 1 .18 52 «D2 eel 1.66
Black bullhead 22 4.11 14.92 .67 3.17
Channel catfish * 21 3.92 38.15 1.81 8,12 1.92
Flathead catfish * 10 1.86 82.15 8.21 17.49 1.96
White bass * 25 4.67 25.12 1.00 5.35 2.99
Striped bass * 4 74 26.87 6.71 Dale 222
Warmouth * 3 -56 .89 .29 .19 3.64
Bluegill * 58 10.82 4.79 -08 1.02 3.39
White crappie * 13 2.43 4.32 33 292 2.52
Freshwater drum 65 12.13 57.00 87 12.14
SSeS
Total 536 100 .00 469 .73 100 .00
Game Fish * 135 25.18 182.81 38.92
Rough Fish 401 74.82 286.92 61.08
Seining results E. V. Spence Reservoir (Bag 26' x 6! x %-inch-mesh
seine, and 20' x 6' x 1/8-inch-mesh seine).
eee
Species Number Size Range in Inches
Gizzard shad
Threadfin shad
Red shiner
Bullhead minnow
White bass
Tidewater silversides
Mor UW rR
Total 18
eee
--- Page 18 ---
=L6=
Table 10. Striped bass evaluation netting results, October, November and
December, 1973. Nine net units (450' x 3/4"-, 14"-, and 2"-,
square-mesh.
Per Cent Total Wt. Avg. Wt. Per Cent
Species Number By No. Pounds Pounds By Wt.
Longnose gar 13 -49 17 .84 1.37 2.35
Gizzard shad 2110 80.07 180.24 .08 23.79
Threadfin shad 1 .04 .03 .03 -00
Carp 23 88 27.12 1.17 3.58
Rivercarpsucker 74 2.80 94.31 1.27 12.45
Blue catfish * 6 «23 4.97 -82 -65
Black bullhead 2 .08 41 .20 .06
Channel catfish * 58 2.20 57.78 99 7.62
White bass * 184 6.98 114.54 .62 15.12
Striped bass * 142 5.38 250.74 1.76 33.09
Bluegill * 6 «23 38 .06 .05
Largemouth bass * 2 -08 1.38 .69 19
White crappie * 12 -46 7.18 .59 94
Freshwater drum 2 -08 .76 .38 LL
Total 2635 100 .00 757.68 100 .00
Game Fish * 410 15.56 436.97 57 .66
Rough Fish 2225 84 .44 320.71 42.34
--- Page 19 ---
=| 7s
Table 11. Survey results Macho Lake, October 4, 1973.
Results of two standard gill nets, and one large-mesh net.
Per Cent Total Wt. Avg. Wt. Per Cent Average
Species Number By No. Pounds Pounds By Wt. a
Carp 4 3.01 22 .39 5.59 60.36
Channel catfish * 14 10.52 5.94 42 16.02 1.44
Bluegill * 111 83.46 8.41 .07 22.67 3.02
Redear sunfish * 4 3.01 35 08 95 3.23
Total 133 100 .00 37 .09 100.00
Game Fish * 129 96.99 14.70 39.64
Rough Fish 4 3.01 22 .39 60 .36
Seining results Macho Lake (Bag 26' x 6' x k-inch-mesh seine,
and 20' x 6' x 1/8-inch-mesh seine).
Species Number Size Range in Inches
Red shiner 15 4
Mosquitofish 1 45
Green sunfish 19 13/4-33,
Bluegill 49 1-44
Redear sunfish 26 34
Largemouth bass 23 2-5
Total 133
--- Page 20 ---
-18-
Mountain Creek Lake
This small municipal water supply reservoir at Robert Lee was
chemically renovated in 1970 and restocked with desirable game fish.
Drought conditions and low fertility apparently have hampered the
expansion of the fish population. Only 14 fish were collected
with 5 gill nets (Table 12).
No management activities are planned until additional water is
impounded and present conditions changed.
Nasworthy Lake
Lake Nasworthy continues to be one of the most heavily used fishing
and recreation sites in this area. The primary fish species sought
include channel catfish, largemouth bass, and white crappie. Table
13 shows a variety of game fish present, but their numbers have
decreased from past surveys. Due to heavy siltation, very little
suitable game fish spawning area is available. Therefore supple-
mentary bass and catfish stockings have been recommended annually
(Table 3). However, suspension of largemouth bass stockings is
recommended to determine the natural reproductive success. White bass
x striped bass hybrids are also recommended to add an open-water
predator as well as a sport fish.
North Concho Reservoir
This U.S. Corps of Engineers reservoir has failed to receive any
significant run-off in the past two years and is less than one-tenth
its capacity (this reservoir was dry in 1970). The game fish stocked
since 1971 have shown good survival and growth. The hatchery-stocked
flathead catfish have increased from fingerling size to over 5 pounds
average weight.
Walleye are also a major part of the fish population, accounting for
10.41% by number and 28.67% by weight of the combined netting results
(Table 14). Although walleye are present in significant numbers they
are rarely taken by fishermen. However, some local fishermen have
learned to catch them indicating that an educational campaign might
help increase the walleye harvest.
Oak Creek Lake
This deep, clear 2,300-acre reservoir is the municipal water supply for
the city of Sweetwater. It also provides public recreation and generator
coolant water for West Texas Utilities Company. This segment's survey
results (Table 15) show game species well represented, as nine desirable
species accounted for about one-third of the netting sample by weight
and number. Largemouth bass continues to be the most popular species
and many trophy bass are taken regularly.
--- Page 21 ---
==
Table 12, Survey results Mountain Creek Lake, April 5, 1973.
Results of four standard gill nets, and one large-mesh net.
Per Cent Total Wt. Avg. Wt. Per Cent Average
Species Number By No. Pounds Pounds By Wt. A
River carpsucker 1 7.14 2.47 2.47 27 .97
Black bullhead 8 57.14 1.07 13 12.12
Channel catfish * 3 21.43 3.52 1.17 39.86 1.70
Largemouth bass * 2 14.29 1.77 .88 20.05 2.74
a
Total 14 100.00 8.83 100 .00
Game Fish * 5 35.72 5.29 59.91
Rough Fish 9 64.28 3.54° 40.09
Eee
--- Page 22 ---
Table 13. Survey results Nasworthy Lake, August 23, 24, 1973.
Results of twelve standard gill nets, and four large-mesh nets.
Per Cent Total Wt. Avg. Wt. . Per Cent Average
Species Number by No. Pounds Pounds By Wt. "KM
Longnose gar 4 3 11.72 2.93 3.45
Gizzard shad 494 66.13 96 .00 19 28.31
Carp 55 7.36 96.00 1.74 28.31
River carpsucker 10 1.34 34.00 3.40 10 .02
Blue catfish * 1 14 19 wL9 -06 1.44
Channel catfish * 42 5.61 63 .68 1.51 18.78 1.2/8
Flathead catfish * 1 14 2.86 2.86 .84 1.93
White bass * 2 «lt 2.64 1.32 .78 2.87
Bluegill * 49 6.56 4.57 09 1.35 3.5
Redear sunfish * Ll 1.47 88 08 26 Zah2
Largemouth bass * 3 40 2.05 .68 .60 2.42
White crappie * 52 6.97 13 .84 26 4.08 2.55
Freshwater drum 23 3.08 10.69 46 3.16
Total 747 100 .00 339 .12 100 .00
Game Fish * 161 21.56 90.71 26.75
Rough Fish 586 78,44 248.41 73.25
-~20-
Seining results Nasworthy Lake, (Bag 26' x 6' x }-inch-mesh
seine, and 20' x 6' x 1/8-inch-mesh seine).
Species
Gizzard shad
Threadfin shad
Golden shiner
Red shiner
Bullhead minnow
Mosquitofish
Bluegill
Redear sunfish
Largemouth bass
Total
Number
PPE RPNNFNE
12
Size Range in Inches
nt oe
!
lo
Nh
av
Sonne Fresh
net or
i
{
t
i
H
j
_
a
--- Page 23 ---
==
Table 14. Survey Results North Concho Lake, March 9, 1973 and June 7, 1973.
Results of eleven standard gill nets and two large-mesh nets.
Per Cent Total Wt. Avg. Wt. Per Cent Average
Rr a ee pe
Species Number By No. Pounds Pounds By Wt. UKE
Gizzard shad 142 36.04 36.59 .25 11.97
Carp 66 16.75 17.12 «25 5.60
River carpsucker 56 14.21 63.55 1.13 20.79
Smallmouth buffalo 2 51 1.65 -82 54
Black bullhead 31 7.87 6.33 -20 2.07
Channel catfish * 23 5.83 39.13 1.70 12.80 2.21
Flathead catfish * 8 2.04 41.74 5a 21 13.66 2.67
White bass * 3 .76 4.66 1.55 1.53 3433)
Green sunfish * 1 29 »15 oh 04 3.99
Orangespotted sunfish* 1 25 .08 -08 -03 5.07
Bluegill * 13 3430 1.01 -07 «33 4.24
Largemouth bass * 3 ./6 2.48 .82 81 2.82
White crappie * 2 Ol 223 ell .08 2.86
Walleye * 41 10.41 87 .62 2213 28.67 1.79
Freshwater drum 2 Ol 3.30 1.65 1.08
OO eee eee ee
Total 394 100.00 305.64 100.00
Game Fish * 95 24.11 177.10 57.95
Rough Fish 299 75.89 128.54 42.05
eee
Seining results North Concho Lake, (Bag 26' x 6' x 4%,-inch-mesh
seine, and 20' x 6' x 1/8-inch-mesh seine).
eee
Species Number Size Range in Inches
a ,
Gizzard shad 301 45-6
Threadfin shad 3 4-1
Carp 51 5-7
Red shiner 42 1-2
Mosquitofish Ll 1
Green sunfish 4 1-3
Orangespotted sunfish 1 3
Bluegill 24 -5
Longear sunfish
Redear sunfish
Largemouth bass
TT
Total 445
Rr Ww
PN perve
t ne
(oe) 1
wo
--- Page 24 ---
=2
2=
Table 15. Survey results Oak Creek Lake, April 18, 19, 1973 and
April 27, 1973. Results of 18 standard gill nets and
6 large-mesh nets.
Per Cent Total Wt. Avg. Wt. Per Cent Average
Species Number by No. Pounds Pounds __by Wt. mK
Gizzard shad 253 36.24 51.45 -20 9.18
Carp 48 6.88 100.00 2.08 17.85
River carpsucker — 179 25.64 206 .00 1.15 36.77
Black bullhead 2 .29 .82 41 14
Channel catfish * 11 1.58 17.67 1.60 3.16 1.62
Flathead catfish * 5 71 62.17 12.43 11.09 2.14
White bass * 40 5.43 68.65 1.71 12.26 2.90
Redbreast sunfish * 1 LS .52 52 .09 4.56
Green sunfish * 1 15 .09 -09 .02 3<51
Bluegill * 84 +202 7.16 .08 1.27 3.10
Longear sunfish * 2 .29 15 .07 .03 3.53
Redear sunfish * 8 1.15 Od -07 ell 3.15
Largemouth bass * 12 1.72 30.33 2.52 5.42 2.64
White crappie * 52 7.45 14.62 28 2.61 2.56
Total 698 100 .00 560.25 100 .00
Game Fish * 216 30.95 201 .98 36.06
Rough Fish 482 69 .05 358.27 63.94
Seining results Oak Creek Lake (Bag 26' x 6' x }-inch-mesh
seine, and 20' x 6' x 1/8-inch-mesh seine).
Species Number Size Range in Inches
Red shiner
Blacktail shiner
Total
a
--- Page 25 ---
-23-
The clear water of this reservoir has permitted heavy growth of
submerged vegetation which interferes with boating and fishing. A
total chemical treatment is not feasible because it is a municipal
water supply. However, spot chemical treatments and mechanical
controls are being considered.
Channel catfish fingerlings are stocked annually, and recoveries of
marked specimens (under Job 14 of this project) confirm good survival.
Red Bluff Lake
In most years, centrarchid reproduction at Red Bluff is low or non-
existent because of the high salinity of the water. However, a
large inflow of fresh water in the spring of 1973 allowed a success-
ful largemouth bass spawn, and young-of-the-year bass were seined in
the upper end in October. Table 16 summarizes survey results from
June and October, 1973.
Interviews with at least 20 fishermen indicate that the harvest rate
of largemouth bass and other game fish is low. The abundance of
threadfin shad and tidewater silversides in Red Bluff, the general
lack of largemouth bass, and the large reservoir size increase the
justifications for stocking striped bass or striped x white bass
hybrids. ;
Robert Lee City Lakes
Located near Robert Lee, these small impoundments once provided muni-
cipal water for the City. Siltation has greatly reduced their
capacities, and they presently serve only as fishing sites. Both were
chemically renovated in 1970 and restocked with game species. The
larger of the two was checked during this segment (Table 17), and
no undesirable species were found. The smaller lake was not netted
due to low water; however, it reportedly supports a sizeable largemouth
bass population.
Management activities will depend on water impoundment and fisherman
utilization.
Twin Buttes Reservoir
The Bureau of Reclamation constructed this impoundment on the Middle
and South Concho Rivers approximately 11 years ago. The first signi-
ficant run-off was received in 1970 as it reached about one-half of
the conservation level. Heavy stocking of channel, blue and flathead
catfish, largemouth bass and walleye followed shortly. Catfish and
walleye stockings have continued annually (Table 3).
This year's survey on Twin Buttes reflects a poor game fish population,
particularly walleye, considering the past stockings. Rough fish, mainly
gizzard shad, carp and carpsucker, accounted for 82.52% number and 93.38%
weight of the netting sample. These figures were considerably higher
than in previous years. Channel catfish, white crappie, and largemouth
--- Page 26 ---
-24-
Table 16. Survey results Red Bluff Reservoir, June 19, 1973 and
October 2, 1973. Results of twelve standard gill nets,
and four large-mesh nets.
Per Cent Total Wt. Avg. Wt. Per Cent Average
Species Number By No. Pounds Pounds By Wt. MK
Longnose gar 63 11.20 155.71 2.47 19.67
Gizzard shad 146 25.98 28.71 19 3.63
Carp 94 16.73 49.97 .53 6.32
River carpsucker 20 3.56 24 .00 1.20 3.03
Smallmouth buffalo 162 28.82 458 .00 2.82 57.88
Channel catfish * 13 2 32 14.38 1.10 1.82 1.56
White bass * 30 5.34 45.92 1.53 5.80 3.04
Green sunfish * 13 2.32 2.27 -17 .29 3.75
Bluegill * 12 2.12 3.28 .27 41 4.44
Largemouth bass * 9 1.61 9.04 1.00 1.15 3.02
Total 562 100 .00 791.28 100 .00
Game Fish * 77 13.71 74 .89 9.47
Rough Fish 485 86.29 716.39 90.53
Seining results Red Bluff Reservoir, (Bag 26' x 6' x }-
inch-mesh seine, and 20' x 6' x 1/8-inch-mesh seine).
Species Number Size Range in Inches
Gizzard shad 188 1-8
Threadfin shad 10 13, - 24,
Carp 256 1-2
Golden shiner 1 2 3/4
Red shiner 205 1-3
Fathead minnow 1 1%
Bullhead minnow 3 14-2
River carpsucker 1 3
Smallmouth buffalo 4 14-5%
Zebra minnow 2 14,-1%
Mosquitofish 5 14-1 3/4
Green sunfish 1 1 7/8
Bluegill i 1
Largemouth bass 2 3
Tidewater silversides 2869 1-43
Total 3549
--- Page 27 ---
-25-
Table 17. Survey results Robert Lee Old City Lake, January 31, 1974.
Results of two standard gill nets.
Per Cent Total Wt. Avg. Wt. Per Cent Average
Species Number By No. Pounds Pounds By Wt. RN
Channel catfish * 2 11.76 8.92 4.46 43.53 2.16
Warmouth * 8 47 .06 1.36 .17 6.64 3 67
Bluegill * 1 5.88 .09 .09 44 3.84
Largemouth bass * 6 35 .30 10.12 1.68 49 .39 3.16
Total 17 100.00 20.49 100.00
Game Fish * 17 100.00 20.49 100 00
Rough Fish
--- Page 28 ---
-26-
bass comprise the primary sport fishery at the present time. Walleye
have been liberally stocked for the past three years but were not
collected during this segment. However, they are occasionally reported
by fishermen.
’
Feasible management practices for this situation appear to be limited
at this time. ,
Valley Creek Lake
Valley Creek Lake provides water for the city of Ballinger. Silta-
tion is becoming a problem in this old reservoir as in many small
West Texas impoundments. However the past two annual surveys have
indicated an increase in the game fish population. Table 19 shows
catfish, white crappie, and largemouth bass well represented in the
netting sample for this lake. No management activites are planned
at this time.
Winters Lake
The turbidity continues to be very high in this shallow city water
supply lake and limits desirable fish production mainly to catfish and
white crappie. Table 20 gives the 1973 survey results which are
similar to past collections. Gizzard shad, carp, and river carpsucker
account for the majority of rough fish. A complete chemical renovation
of the fish population of this lake and its small watershed may be
feasible in the future as a new city water supply is being planned.
Colorado River
The Colorado River was sampled once with gill nets during this segment
in Concho County. There was little sustained flow and no major run-off
had occurred in several months. Table 21 is fairly representative of
the fish population found in most sections of the upper Colorado. Cat~-
fish provide the majority of the sport fishing. Although no seining
samples were made, red shiner and blacktail shiners are usually abun-
dant. No management practices are feasible but sampling should be
done when possible for future reference.
San Saba River
The San Saba River was surveyed twice this segment in Menard and
Schleicher Counties. The combined results are given in Table 22.
Channel and flathead catfish and white crappie are the primary game
fish present and provide the most fishing in this area. Although none
were netted, spotted bass are known to be present and sought after bs
many anglers in this clear stream.
The stocking of marked hatchery fingerling channel catfish job 14 of
this project) is yielding data indicating high levels of survival in
this area of the river.
--- Page 29 ---
-27-
Table 18. Survey results Twin Buttes Reservoir, June 8, 1973.
Results of eight standard gill nets.
Per Cent Total Wt. Ave. Wt. Per Cent Average
Species Number by No. Pounds Pounds by Wt. ie
Longnose gar 25 4.64 55.00 2.20 8.88
Gizzard shad 197 36.62 31.00 15 5.01
Carp 86 15.98 146.00 1.69 23.60
River carpsucker 84 15.62 320.00 3.80 51.72
Gray redhorse sucker 1 .18 1.76 1.76 +29
Channel catfish * 15 2 PQ 25.48 1.69 4.12 LifS
White bass * 5 93 3.07 -61 -49 2.06
Redbreast sunfish * 1 .18 .22 e22 .04 3.15
Green sunfish * 3 .56 30 . 10 .05 2.94
Bluegill * 45 8.37 6.61 .14 1.06 3.70
Longear sunfish * 9 1.67 75 .08 +13 3.16
Largemouth bass * 6 1.12 2 kd 35 134 1.90
White crappie * 10 1.86 2.40 24 39 2.27
Freshwater drum 51 9.48 24 .00 47 3.88
eee eee ee eee
Total 538 100 .00 618.71 100 .00
Game Fish * 94 17.48 40.95 6.62
Rough Fish 444 82.52 577 .76 93 .38
Seining results Twin Buttes Reservoir (Bag 26' x 6' x k-inch-
mesh seine, and 20' x 6' x 1/8-inch-mesh seine).
ee
Species Number Size Range in Inches
rr
Gizzard shad 90 7-8
Golden shiner 51 4-4
Red shiner 78 14-3
Blacktail shiner 25 1-3
Bullhead minnow 1 1
Mosquitofish 53 45-2
Warmouth 1 6
Green sunfish 4 1-3
Bluegill 55 45-14
Longear sunfish 5 1-4
Redear sunfish 2 4-5
Largemouth bass 7 45-8
White crappie 2 1-8
--- Page 30 ---
=28-
Table 19. Survey results Valley Creek Lake, June 6, 1973.
Results of five standard gill nets, and two large-mesh nets.
Per Cent Total Wt. Avg. Wt. Per Cent Average
Species Number By No. Pounds Pounds By Wt. mK
Longnose gar 9 3.73 36.00 4.00 9.59
Gizzard shad 77 31.95 8.92 ell 2.38
Carp 19 7.88 85 .00 4.47 22.67
River carpsucker 59 24.48 76.00 1.28 20.26
Channel catfish * 6 2.49 13.05 2.17 3.48 1.95
Flathead catfish * 7 2.91 91.71 13.10 24.45 2.26
Bluegill * 34 14.11 3.28 .09 -88 3.02
Longear sunfish * 3 1.24 .19 -06 .05 3.55
Largemouth bass * 4 1.66 12.70 3.17 3.38 2.55
White crappie * 17 7.06 7.20 42 1.92 2.44
Freshwater drum 6 2.49 41.00 6.83 10.94
i
Total 241 100 .00 375.05 100 .00
Game Fish * 71 29.47 128.13 34.16
Rough Fish 170 70.53 246.92 65 .84
i
Seining results Valley Creek Lake ( Bag 26' x 6' x %-inch-mesh
seine, and 20' x 6' x 1/8-inch-mesh seine) .
eR
Species Number
a
Gizzard shad 20
Carp 1
Red shiner 10
Blacktail shiner 8
River carpsucker 1
Bluegill 2
White crappie 1
ee
Total 43
i
--- Page 31 ---
-~29-
Table 20. Survey results Winters Lake, June 21, 1973.
Results of four standard gill nets, and two large-mesh nets.
Per Cent Total Wt. Avg. Wt. Per Cent Average
eee
Species Number By No. Pounds Pounds By Wt. KN
Gizzard shad 59 26.57 11.00 .18 5.29
Carp 11 4.96 40 .00 3 263 19.24
River carpsucker 39 17.57 58 .00 1.48 27.90
Smallmouth buffalo 4 1.80 23 «00 5.75 11.07
Black bullhead 4 1.80 1.92 -48 -92
Channel catfish * 24 10.81 19 .06 .79 9.17 1.73
Flathead catfish * 5 2) 25 43.55 8.71 20.95 2.19
Bluegill * 3 1.35 .28 .09 ~L3 4.31
White crappie * 63 28 .38 8.53 -13 4.11 2.44
Freshwater drum 10 4.51 2.53 .25 1.22
eee ee
Total 222 100.00 207.87 100 .00
Game Fish * 95 42.79 71.42 34 .36
Rough Fish 127 57 321 136.45 65.64
Seining results Winters Lake (Bag 26' x 6' x %-inch-mesh seine,
and 20' x 6' x 1/8-inch-mesh seine).
eee
Species Number Size Range in Inches
SSeS
Gizzard shad 70 1-8
Carp 18 3-5
Golden shiner 12 2-24
Red shiner 140 1-3
Channel catfish 1 10
Mosquitofish 60 1
Bluegill 1 4
Longear sunfish 1 2
Redear sunfish 1 4
Largemouth bass uy 1
White crappie 55 45-8
Logperch 3 2~3
eee
Total 363
--- Page 32 ---
-30-
1.51
Lol?
yoy
2 oat
3.07
Table 21, Survey results Colorado River, Concho County, February 135,
Results of two standard gill nets, and one large-mesh net.
Per Cent Total Wt. Avg. Wt. Per Cent Avera:
Species Number By No. Pounds Pounds By Wt.
Longnose gar 28 28.57 80.50 2.87 41.57
Gizzard shad 29 29.59 34.00 1.17 17.56
Carp 2 2.04 12.00 6.00 6.19
River carpsucker 25 25.51 37 .00 1.48 19.11
Smallmouth buffalo 2 2.04 13.00 6.50 6.71
Channel catfish * 3 3.05 4.10 1.36 2.12
Flathead catfish * 1 1.03 6.00 6 .00 3.10
Bluegill * 6 6.11 .56 -09 -29
White crappie * 1 1.03 -48 -48 225
Freshwater drum 1 1.03 6.00 6 .00 3.10
Total 98 100 .00 193 .64 100 .00
Game Fish * 11 11.22 11.14 5.76
Rough Fish 87 88.78 182 .50 94.24
--- Page 33 ---
-31-
Table 22. Survey results San Saba River, June 27, 1973 and October 30,
31, 1973. Results of eleven standard gill nets, and four large-
mesh nets.
Per Cent Total Wt. Avg. Wt. Per Cent Average
Species Number By No. Pounds Pounds By Wt. mK"
Longnose gar L5 3 «61 29.52 1.96 3.22
Gizzard shad 146 35.09 70.68 -48 7.72
Carp 6 1.44 45.00 7.50 4.92
River carpsucker 111 26.68 267 .00 2.40 29.16
Smallmouth buffalo 30 8.42 327.29 9 35 35.75
Gray redhorse sucker 2 -48 4.12 2.06 45
Golden redhorse sucker 1 «24 1.92 1.92 221
Channel catfish * 14 3.36 30.94 2.21 3.38 1.83
Flathead catfish * 6 1.44 40.96 6.82 4.47 1.84
Warmouth * 5 1.21 1.48 .29 -17 3235
Bluegill * 14 3.36 1.25 .08 «13 3 58
Redear sunfish * 2 -48 “OT 28 .06 3.40
White crappie * 44 10.58 14,11 32 1.55 2.79
Freshwater drum 15 3.61 80.65 5.37 8.81
Total 416 100 .00 915.49 100.00
Game Fish * 85 20.43 89.31 9.76
Rough Fish 331 79.57 826.18 90.24
Se
Seining results San Saba River (20' x 6' x 1/8-inch-mesh seine).
ere pn nn ee
Species Number Size Range in Inches
Gizzard shad 50 1-6
Red shiner 10 235
Sharpnose shiner 75 45-2
Spottail shiner 2500 45-3
Gray redhorse 1 3
Channel catfish 1 2
Mosquitofish 30 1-14
Redbreast sunfish 25 2-3
Green sunfish 1 3
Bluegill 5 2-3
Spotted bass 50 2-6
Largemouth bass 12 2-3
White crappie 2 2
Total 2762
a nr
--- Page 34 ---
=39-
It is recommended that this supplementary stocking be continued in
the upper portions of the San Saba to provide a better fishery.
General Conclusions, Discussion and Recommendations
Low water conditions and heavy siltation are adversely affecting game fish
production in many of the smaller Region I-B lakes. Supplementary stocking
has shown improvements in some cases.
Sound fisheries management practices for larger reservoirs are limited in
most instances. However, the stocking of large predator species is pro-
viding additional fisheries benefits at E.V. Spence and North Concho Lakes.
The stocking of striped bass or white-striped bass hybrids should be
attempted in the more troublesome West Texas reservoirs. However it is
recommended that part-time creel clerks be employed at each of the lakes to
be stocked before management introductions are made.
V. Prepared by: Billy J. Follis
Project Leader
Date: March 26, 1974 Leo Lewis __
Regional Director, Inland Fisheries
Region IT
, ; t. -
Approved: CLA Jom, ¢ ey Z
~Dingell-Johnson Coordinator
--- Page 35 ---
233.
Achecklist of scientific names is presented so that common names may be used
in this report. These names are specified in "A List of Common and Scientific
Names of Fishes from the United States and Canada", Second fdition, American
Fisheries Society, Special Publication Number 2, 1960.
Common Names
Spotted gar
Longnose gar
Gizzard shad
Threadfin shad
Mexican tetra
Carp
Golden shiner
Red shiner
Sharpnose shiner
Blacktail shiner
Fathead minnow
Bullhead minnow
River carpsucker
Smallmouth buffalo
Gray redhorse
Golden redhorse
Blue catfish
Black bullhead
Channel catfish
Fathead catfish
Vareigated cyprinodon
Zebra minnow
Mosquitofish
White bass
Striped bass
Warmouth
Redbreast sunfish
Green sunfish
Orangespotted sunfish
Bluegill
Longear sunfish
Redear sunfish
Spotted bass
Largemouth bass
White crappie
Black crappie
Walleye
Logperch
Freshwater drum
Tidewater silversides
Scientific Names
Lepisosteus oculatus
Lepisosteus osseus
Dorosoma cepedianum
Dorosoma petenense
Astyanax mexicanus
Cyprinus carpio
Notemigonus crysoleucas
Notropis lutrensis
Notropis oxyrhynchus
Notropis venustus
Pimephales promelas
Pimephales vigilax
Carpiodes carpio
Ictiobus bubalus
Moxostoma congestum
Moxostoma erythrurum
Ictalurus furcatus
Ictalurus melas
Ictalurus punctatus
Pylodictis olivaris
Cyprinodon variegatus
Fundulus zebrinus
Gambusia affinis
Roccus chrysops
Roccus saxatilis
Chaenobryttus gulosus
Lepomis auritus
Lepomis cyanellus
Lepomis humilis
Lepomis macrochirus
Lepomis megalotis
Lepomis microlophus
Micropterus punctulatus
Micropterus salmoides
Pomoxis annularis
Pomoxis nigromaculatus
Stizostedion vitreum
Percina caprodes
Aplodinotus grunniens
Menidia beryllina