TPWD 1974 F-2-R-21 #1598: Fisheries Studies, Region 5-B: Fisheries Management Recommendations, Project F-2-R-21
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PERFORMANCE REPORT
As required by
FEDERAL AID IN FISHERIES RESTORATION ACT
TEXAS
Federal Aid Project F-2-R-21
Fisheries Studies, Region 5-B
Objective B-26: Fisheries Management Recommendations
Project Leader: D. Wade Butler
Assistant Leader: James Lasswell
' Clayton T. Garrison
Executive Director
Texas Parks and Wildlife Department
Austin, Texas
Lonnie J. Peters Robert J. Kemp, Director
Chief, Inland Fisheries Fish and Wildlife Division
March 11, 1974
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ABSTRACT
Public hearings were held to discuss changes in fishing regulations in
regulatory counties. No major changes were proposed. Surveys were conducted
on four of the major reservoirs in Region 5-B: Lakes Canyon, Travis, Lyndon
B. Johnson, and Inks. All lakes revealed little change in the fish popula-
tions over the previous two years. Seining collections indicate poor large-
mouth reproduction or survival in Lakes Lyndon B. Johnson and Inks.
Striped bass were stocked in Lakes Canyon and Travis this segment.
Surveys indicate survival of the stockings and good growth since stocking.
Walleye were stocked in Lakes Canyon and Lyndon B. Johnson, The species
appears to be doing well in both lakes with individuals collected in excess
of one pound after nine months growth.
Management recommendations include;
l. The stocking of threadfin shad in all lakes for additional forage.
2, The continuing of surveys on Lakes Canyon, Travis, and Lyndon B.
Johnson to evaluate the introduction of striped bass and walleye.
3. Investigation of methods to construct artificial cover in Lake
Lyndon B. Johnson through the cooperation of area fishermen.
4. The stocking of smallmouth bass in Canyon Lake.
5. The development of standard management procedures and methods for
collecting management data.
6. The stocking of walleye in Lake Inks.
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State:
Project Title: Fisheries Studies, Region 5-B
PERFORMANCE REPORT
Texas Project Number: F-2-R-21
Project Section: Research and Surveys
Study
Title: _Fisheries Management Recommendations
Contract Period: February 1, 1973 to January 31, 1974 _ _ _
Program Narrative Objective Number: B-26
Objective: To situate fishery management practices in the public waters
I.
Il.
of Region 5-B
Segment Objectives:
A. To propose fish harvest regulations for the waters of Region 5-B.
B. To recommend renovation or population control for waters which
do not provide adequate sports fishing.
C. To recommend supplemental stocking of hatchery reared fish in
newly impounded reservoirs, renovated reservoirs, waters that
have sustained major fish kills, and waters which have had
negligible natural reproduction.
D. To determine vegetation control needs.
E. To determine public access needs.
Summary of Progress:
Proposed fishing regulations were presented to the public in those
counties in Region 5-B under regulatory authority. No major changes
in the regulations were proposed for the Edwards Plateau, Possum
Kingdom, and Trinity-Brazos Regulatory Districts.
Quarterly surveys were conducted on Lakes Canyon, Travis, Lyndon B.
Johnson, and Inks. Experimental gill nets, 150 feet in length and
8 feet in depth, were utilized at stations located to uniformly cover
the lakes. Gill net mesh sizes ranged from 1 inch to 34 inches increasing
% inch every 25 feet of length. The number of nets set on a particular
lake depended upon the size of the lake surveyed. Seine samples were
collected at various times between June and October on each lake with a
20 foot by 4 foot common sense minnow seine having a mesh size of 3/8-inch.
Water samples were collected during surveys as well as information con-
cerning needs for vegetation control and public access.
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Lake Canyon
Lake Canyon is a 8,240 surface acre lake constructed in a limestone
basin on the eastern reaches of the Edwards Plateau in Comal County.
The lake impounds waters of the Guadalupe River drainage basin com-
posed primarily of spring waters and runoff from the Edwards Plateau.
Lake Canyon is a relatively deep lake with a maximum depth of 125 feet
and an average depth of 47 feet. Constructed and controlled by the
U.S. Corps of Engineers, the impounded waters are discharged from a
depth of 125 feet and provide a cold water fishery in the tailrace.
Lake use is primarily for water conservation, flood control, irrigation,
and recreation. Lake Canyon exhibits a monolithic pattern, stratifying
in normal years by June and destratifying by October.
Lake Canyon was surveyed quarterly during 1973 with a total of 1,225
fish collected weighing 2,030.12 pounds. A total of 60 experimental
gill nets were set in the four surveys. Rough fish represented 60.90
percent by number and 60.19 percent by weight of the total fish collect-
ed with the remainder game fish and sunfish (Table 1). The data in-
dicates very little change in the overall population during the past
three years when expressed in catch per unit effort (Figure 1). White
bass (Morone chrysops) were collected in regular quarterly surveys
for the first time although anglers have reported catches during the
past two years. A limited number of mature white bass were collected
in the surveys, but larger numbers of young individuals were collected
in monofilament gill nets during striped bass surveys conducted in
October, November, and December. It appears that there is a strong
first year age class of this species present in Lake Canyon and it is
expected that an excellent white bass fishery will develop by next
year. The data also reflects good populations of channel catfish,
flathead catfish, white crappie, and largemouth bass.
The gray redhorse sucker (Moxostoma congestum) and gizzard shad
(Dorosoma cepedianum) remain the dominant rough fish in Lake Canyon.
These two species contributed over 50 percent of the total number of
fish collected and over 30 percent of the biomass. However, Canyon
still reflects a better rough-game fish balance than other lakes in the
area.
A total of 20,000 striped bass fingerling were stocked in Lake Canyon
during July. Survival was documented two weeks later when seven stripers
were collected in routine seining collections. Striped bass surveys
produced a total of 47 stripers during the three months of surveys with
the stripers averaging eight ounces in the December collections.
Present plans call for the stocking of striped bass in Lake Canyon for
two additional years at a rate of 10 per surface acre.
Approximately 625,000 walleye fingerling were also stocked in Lake
Canyon during April. No walleye were collected until October at which
time a nine ounce walleye was collected in a monofilament gill net used
in the striped bass surveys. No walleye have appeared as of yet in
regular quarterly surveys, but a total of 27 walleye were collected in
the three months of striper surveys. The largest walleye collected to
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Table 1
Results of Canyon Lake Gill Netting for 1973
60 Nets Set
Percent Percent
of Weight of Average
Species Number Numbers (Pounds) Weight —-— Weight _
Longnose gar 42 3.43 102.70 5.06 2.45
Gizzard shad 314 25.63 156.89 7.73 0.50
Golden shiner 5 0.41 1.59 0.08 0.32
Carp 69 5.63 416.26 20.50 6.03
River carpsucker 9 0.73 37.08 1.83 4.12
Gray redhorse sucker 305 24.90 506.80 24.96 1.66
Channel catfish* LL? 9.95 261.74 12.89 2.24
Flathead catfish* 62 5.06 409.76 20.18 6.61
White bass* 12 0.98 16.88 0.83 1.41
Largemouth black bass* 45 3.68 42.56 2.10 0.95
Warmouth sunfish* 7 0.57 2.59 0,13 0.37
Green sunfish* 17 1.39 2651 0.12 0.15
Redbreast sunfish* 5 0.41 0.94 0.05 0.19
Bluegill sunfish* 47 3.84 7.13 0..35 0.15
Redear sunfish* 140 11.43 58.63 2.89 0.42
Longear sunfish* 2 0.16 0.38 0.02 0.19
White crappie* 25 2.04 5.12 0.25 0.20
Rio Grande perch 2 0.16 0.56 0.03 0.28
Total 1,225 100.00 2,030.12 100.00
* Designates Game Fish Species eee
Percent of catch by: Number Weight
Rough fish = 60.90 60.19
Game fish = 21.31 36.26
Sunfish = 19.29 3.55
Catch per 100 feet of net: Number Weight
Rough fish = 8.29 13%58
Game fish = 2.90 8.18
Sunfish = 2.42 0.80
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Catch per 100 Feet of Net
Catch per 100 Feet of Net
1971 1972 1973
Years
CANYON LAKE
Figure 1. Comparison of the average catch (weight and nunber)
of rough fish, game fish, and sunfish per LOO feet of gill net
during the years 1971, 1972, and 1973 in Canyon Lake. There were
three or more gill netting surveys conducted each year.
25 EEE) Pounds Rough Fish
1 Pounds Game Fish
20 (__] Pounds Sunfish
@8 Numbers
15
10
5
0 :
1971 1972 1973
Years
LAKE TRAVIS
Figure 2. Comparison of the average catch (weight and number)
of rough fish, game fish, and sunfish per 10° feet of gill net
during the years 1971, 1972, and 1973 in Lake Travis. There were
three or more gill netting surveys conducted each year.
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date measured 14.5 inches and weighed 1 pound and 2 ounces. Sexual
development was observed in a few male and female individuals and the
possibility of limited reproduction occurring this season is being
investigated.
Seining data reflects acceptable largemouth bass reproduction and
survival in 1973 (Table 2). Good numbers of small forage species
were also collected, with red shiners, blacktail shiners, mosquitofish,
and silversides the dominant species. Additional forage, small shad
and sunfish, should be available during the spring and early summer,
but with the introduction of striped bass and walleye, other forage
species are being considered.
Lake Canyon has not experienced vegetation problems since impoundment.
Although the water is generally very clear, there are few shallow areas
that could present vegetation problems to fishermen.
Public access will probably never be a problem on Lake Canyon.
Numerous concrete launching facilities are available throughout the
lake at the various public parks constructed and maintained by the
U.S. Corps of Engineers. Camping, swimming, and bank fishing areas
are also available within these parks.
Lake Travis
Lake Travis is a large, meandering lake with a normal pool of 18,930
surface acres, impounding waters of the Colorado River in Travis County.
Lake Travis is a deep lake with a maximum depth of 192 feet and a mean
depth of 62 feet. Constructed in 1940 by the Lower Colorado River
Authority, the impoundment is used for flood control, irrigation,
hydroelectric power, recreation, and municipal and industrial water supply.
Lake Travis was also surveyed quarterly during this segment. Due to the
large size of the lake, additional netting stations were established.
A total of 95 gill nets yielded 1,695 fish weighing 3,763.72 pounds.
Gizzard shad contributed the greatest number and smallmouth buffalo the
greatest biomass. Game species made up 28.97 percent by number and 30.69
percent by weight of the total fish collected with white bass account-
ing for 11.8 percent of the total fish (Table 3). Catch per unit effort
calculations indicate an increase in rough fish over 1972, but approxi-
mately the same as 1971 (Figure 2). Since the average weights remained
relatively the same throughout this period, it is doubtful that an in-
crease in 1973 or a decrease in 1972 actually occurred. It is more
likely that this was a result of the sampling techniques and collection
times.
Seining collections were made on Lake Travis from June through
September. It appears that largemouth bass reproduction was success-
ful and survival was good through September (Table 4). A total of
155 young-of-the-year largemouth bass were collected in the June
samples with an average of 2.98 per seine haul decreasing to .25 per
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Species
Notropis texanus
Notropis venustus
Notropis lutrensis
Campostoma anomalum
Gambusia affinis
Menidia beryllina
Notemigonus crysoleucas
Dorosoma cepedianum
Percina caprodes
Pimephales vigilax
*Lepomis auritus
*Lepomis macrochirus
*Lepomis microlophus
*Chaenobryttus cyanellus
Carpiodes carpio
*Micropterus salmoides
*Pomoxis annularis
*Morone saxatilis
*Ictalurus punctatus
* Denotes game species
Table 2
Seining Results - Lake Canyon
June July
(28 hauls) (18 hauls)
| Ue ue
( Yo 3 Vv 3 ;
ao ag |
G Gi :
{ uy u uu u :
2 oe | 8 O8 |
& 6 & Bo |
' =) 3 0 =) 2 Yo 4
Z2 Zo 2 2m }
—— it —L
3 12 -
189 6.75: 378 |21.00
10 36 24 1.33
6 | .21° - -
3 oll! 124 6.89 :
74 2.64: 109 6.06 |
7 2D) = -
190 6.78: = =
18 064: = =
67 | 2.39: 2 11 |
69 |2.46; 3 | .17
14; .50' = -
1) .04, - =
2 | .07) - a
64 2.29) 17 4
16 | .57) 2 4] .1L:
October
(22 hauls)
wad
oe 3
us
&
u u
g 32
E Bed
| 3
Zi Zo
- | - |
140 | 6.36
62 , 2.82
ll 50
7 3) 432
7 | .32:
1 04
17 ~/7
18 82
1 04
9 | .41
2 09
Totals
--- Page 9 ---
Table 3
Results of Lake Travis Gill Netting for 1973
95 Nets Set
Average
Weight _
3422
0.61
3.01
2.71
1.68
12.41
2.29
2.78
7.67
1.33
0.87
2.13
0.23
0.16
0.31
0.23
Percent
of
Species Number Number
Longnose gar 64 3.78
Gizzard shad 488 28.79
Carp 78 4.60
River carpsucker 275 16.22
Gray redhorse sucker 47 2.77
Smallmouth buffalo 78 4.60
Channel catfish* 47 2.77
Blue catfish* 18 1.06
Flathead catfish* 69 4.08
White bass* 200 11.80
Largemouth black bass* 82 4.84
Spotted black bass* 53 3.13
Warmouth sunfish* 5 0.29
Green sunfish* 21 1.24
Redbreast sunfish* 13 0.77
Bluegill sunfish* 76 4.48
Lonzear sunfish* 19 1.12
White crappie* 22 1.30
Rio Grande perch 16 0.94
Freshwater drum 24 1.42
Total 1,095 100.00
* Designates Game Fish Species
Percent of catch by: Number Weight
Rough fish = 63.13 68.58
Game fish = 28.97 30.69
Sunfish = 7.90 — 0.73
Catch per 100 feet of net: Number Weight
Rough fish = 7.51 18.11
3.45 8.11
0.94 0.19
Game fish
Sunfish
i]
Percent
Weight of
(Pounds) Weight
206.00 5.47
296.91 7.89
234.41 6.23
744.76 L9 wf9
79.05 2.10
967.67 25.70
107.74 2.86
50.04 1.33
529.01 14.06
23.33 7.05
71.73 1.91
112.86 3.00
1.13 0.03
3.33 0.09
3.99 O.1l
17.12 0.45
2.05 0.05
18.32 0.49
3.70 0.10
48.57 La29
35 /03642 100.00
--- Page 10 ---
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--- Page 11 ---
seine haul in September. Small forage species are abundant, but it is
felt that additional forage such as threadfin shad could be of benefit
to largemouth bass.
A total of 126,000 striped bass fingerling were stocked in Lake Travis
during July, 1973. To date no stripers have been collected in quarterly
surveys, but 15 stripers were taken in the course of striped bass sur-
veys. December collections produced striped bass averaging 11 ounces
in weight. Stripers will be stocked in Lake Travis for two additional
years in an attempt to establish a reproducing population.
There are few areas in Lake Travis with any significant growth of
aquatic vegetation and no control measures are needed on this lake at
this time.
Public access to some parts of Lake Travis is a problem due to the
morphology of the lake itself. Much of the shoreline consist of
large bluffs and private property not lending itself to bank fishing.
There are few concrete boat launching facilities available for a lake
of this size. Two public parks maintained by the Lower Colorado River
Authority and numerous resort areas have launching facilities, but many
are not usable during periods of low water level. Additional facilities
would be desirable but the improvement of the existing launches would
be of considerable help.
Lake Lyndon B. Johnson
Lake Lyndon B. Johnson is a 6,375 surface acre lake impounding waters
of the Colorado and Llano Rivers. The constant level reservoir dis-
charges through turbines into Lake Marble Falls and receives water
from Lake Inks immediately upstream. Lake Lyndon B. Johnson and Inks
Lake differ from the other lakes in the Colorado River lake chain in
that they both lie upon granite basins between Llano and Burnet Counties,
Lake Lyndon B. Johnson is controlled by the Lower Colorado River Au-
thority and its waters are used for recreation and hydroelectric power.
A steam generator plant is now under construction near Lake Lyndon B.
Johnson and is to be completed in 1974. Water from the lake will be
used in the cooling of the condensors within the plant resulting in a
thermal discharge into the lake. Studies are presently being conducted
by the University of Texas to determine the effects of this effluent
upon the aquatic life. Lake Lyndon B. Johnson was chemically renovated
in April, 1971, and restocked with largemouth bass fry, channel catfish
fingerling, and 150 adult flathead catfish.
Four surveys were conducted on Lake Lyndon B. Johnson during this
segment. A total of 69 gill nets resulted in the collection of 1,622
fish weighing 1,992.12 pounds. This represents a composition of
69.67 percent rough fish by number and 67.92 percent by weight (Table 5).
Figures 3 and 4 graphically illustrate the catch per unit effort since
renovation, indicating a decrease of all groups in numbers but an in-
crease in the average weights since 1972. The river carpsucker continues
--- Page 12 ---
-l0-
Table 5
Results of Lake Lyndon B. Johnson Gill Netting for 1973
Weight
_(Pounds) _
479.44
89.23
186.39
469.43
17.11
190.22
1.13
100.04
231.07
174.05
40.60
4.12
3.11
0.43
4.74
0.19
1.25
73.81
0.94
4.63
1,992.12
Percent
of
__Weight _
19.04
4.48
9.36
23.55
0.86
9.55
0.06
5.02
11.60
8.74
2.04
0.21
0.16
0.02
0.24
0.01
0.06
3.71
0.05
Average
____ Weight
2.56
0.34
2.36
1.12
0.61
1.08
2.82
1.37
4.13
1.39
1.31
0.41
0.22
0.16
O19
O.11
0.57
0.94
ee eee
* Designates Game Fish Species i ceri
69 Nets Set
Percent
of
Species Number Number
Longnose gar 148 9.12
Gizzard shad 259 15.97
Carp 79 4.87
River carpsucker 419 25.83
Gray redhorse sucker 28 1.73
Smallmouth buffalo 176 10.85
Black bullhead catfish 4 0.25
Channel catfish* 73 4.50
Flathead catfish* 56 3.45
White bass* 125 7.71
Largemouth black bass* 31 1.91
Warmouth sunfish* 10 0.62
Green sunfish* 15 0.93
Redbreast sunfish* 2 O12
Bluegill sunfish* 30 1.85
Redear sunfish* lL 0.06
Longear sunfish* 11 0.68
White crappie* 129 7.95
Black crappie* 1 0.06
Walleye* 17 0.49
Freshwater drum_ a 1.05 20019
Total 1,622 100.00
Percent of catch by: Number Weight
Rough fish = 69.67 67.92
Game fish = 26.08 31.38
Sunfish = 4,25 0.70
Catch per 100 feet of net: Number Weight
Rough fish = 10.92 13.07
Game fish = 4.09 6.04
Sunfish = 0.67 0.13
--- Page 13 ---
-ll-
25 G59 Pounds of Rough Fish
E F""2] Pounds of Game Fish
20} {[ -.3} Pounds of Sunfish
° W Number
©
2 15
°o
°
_ 10
o
a.
Ss 5
a
3
rw)
1972 1973
Years
LAKE L.B.J.
Py
o
z
~ 20;
fe] :
{
|
ve 15;
©
=
. 1}
(+5) a
.
3
Y
0 4 BS
1971 1972 1973
Years
INKS LAKE
Figures 3 & 4 Comparison of the average catch (wei;ht and
figures e : #
number) of rough fish, same fish, and sucfish per 199 feet Of fits
net during the vears 1971, 1972, and 1773 in Lakes u.Bed. and Lake
Tinire
LYS «
--- Page 14 ---
=]2-
to be the dominant rough fish as was the case prior to renovation. The
carpsucker contributed the greatest numbers and biomass of the rough
fish and total fish while the white bass represented the greatest num-
ber of game fish. It appears that flathead catfish have reestablished
with a total 56 collected averaging 4.13 pounds. The data also in-
dicates a good population of white crappie with this species repre-
senting almost 8 percent of the total catch.
Only 31 largemouth bass were collected in the surveys representing
1.91 percent of the total fish. This compares with 85 collected in
1972 comprising 4.05 percent. It is not clear what the cause of de-
crease could have been other than the absence of desirable habitat.
The lowering of the lake prior to renovation revealed the absence of
cover condusive to good bass populations and very little vegetation
has returned to the lake to provide additional cover.
Red shiners, blacktail shiners, and silversides are the most abundant
small forage in Lake Lyndon B. Johnson (Table 6). The seining data
also indicates limited natural reproduction or survival of the large-
mouth bass. A total of 48 seine hauls yielded only five young-of-the-
year largemouth bass.
A total of six million walleye fry were stocked in Lake Lyndon B.
Johnson during April, 1973. Survival from the stocking was documented
in June when four 34-inch walleye were collected in seining collections.
Quarterly surveys in October produced 17 walleye averaging nine ounces
in weight and measuring 9 to 12 inches. Walleye will be stocked in
Lake Lyndon B. Johnson for two additional years.
Lake Lyndon B. Johnson is free from any problem vegetation. Shallow
areas have either sand or solid granite bottoms prohibiting the growth
of most macrophytes. No vegetation control measures are needed on Lake
Lyndon B. Johnson at the present time.
Existing public access is adequate for Lake Lyndon B. Johnson. There
are numerous boat launching facilities and bank fishing areas in the
various resorts on the lake although private property does limit bank
fishing to some degree. .
Lake Inks
Lake Inks is an 803 surface acre lake maintaining a constant level
and impounding waters of the Colorado River discharged from Lake
Buchanan located immediately upstream. The lake is a relatively
shallow lake with a mean depth of only 23 feet. The lake is controlled
by the Lower Colorado River Authority and is used primarily for
recreation and hydroelectric power.
A total 30 overnight, bottom gill nets were set in Lake Inks this
segment resulting in the collection of 963 fish weighing 2,128.73
pounds (Table 7). The data indicates a high composition of rough
--- Page 15 ---
-13-
Table
6
Seining Results - Lake Lyndon B. Johnson
Species
Notropis venustus
Notropis lutrensis
Menidia beryllina
Dorosoma cepedianum
*Lepomis auritus
*Lepomis macrochirus
*Lepomis microlophus
*Lepomis megalotis
*Chaenobryttus cyanellus
Percina caprodes
*Micropterus salmoides
*Stizostedion vitreum
ale
w
Denotes Game Species
| June
| (7 hauls)
om
on
ag
a
4 4
| 2 ae
g Bed
5 3 0
| Zo
40 5.71
52 7.43
473 | 67.57
1 14
7 +} 1.00
8 1.14
1 | 14
5 71
4 257
July
(27 hauls) |
ue |
os. |
as |
G
My Se
dD) cd) y |
2 25)
=) 3 oO
a an)
a
375 | 13.89)
78 2.89 |
1338 | 49.55)
1 £04 |
1 04 |
32 1.18)
1 04
11 AL
4 15
2 .07
- - |
September
(14 hauls)
od
()
a @
pcs
u u
g 32
& Ged
3 boo a (D) ‘
ea an i
60 4.29
22, 1.57
449 (32.07
7 7 = |
14.) 1.07 |
24) 1.71
_ i = :
i l
2 | .14
1 | .07
1 | .07
3! 21
= \ =
|
|
|
i a F
Totals
475
152
2260
22
64
ht
POrFWU@Oh
--- Page 16 ---
= hiZ<
Table 7
Results of Inks Lake Gill Netting for 1973
30 Nets Set
Percent Percent
of Weight of Average
Species Number Numbers (Pounds) ———s Weight _ Weight _
Longnose gar 16 1.66 62.42 2.93 3.90
Gizzard shad 356 36.97 124.93 5.87 235
Carp 21 2.18 78.48 3.69 3.74
River carpsucker 205 21.29 804.68 37.80 3.92
Gray redhorse sucker di 0.10 4.50 0.21 4.50
Smallmouth buffalo 70 Vedl 662.67 31.13 9.47
Channel catfish* 45 4.67 53.26 2.50 1.12
Flathead catfish* 11 1.14 111.98 5.26 10.18
White bass* 84 8.72 143.99 6.76 1.74
Largemouth black bass* 19 1.97 31.93 1.50 1.68
Spotted bass* 17 1.77 17.13 0.80 1.01
Warmouth sunfish* 5 0.52 1.05 0.05 e21
Green sunfish* 13 1.35 2.42 0.11 19
Redbreast sunfish* 7 0.73 0.81 0.04 ell
Bluegill sunfish* 50 5.19 6.12 0.29 wd2
Redear sunfish* 7 0.73 1.39 0.07 -20
Longear sunfish* 24 2.49 2.37 O.11 -10
White crappie* 5 0.52 4.60 0.22 .92
Freshwater drum 7 C—O 14.00 ————0, 66 ____-2.00
Total 963 100.00 2,128.73 100.00
* Designates Game Fish Species
Percent of catch by: Number Weight
Rough fish = 70.20 © 82.29
Game fish = 18.80 17.05
Sunfish = 11.00 0.66
Catch per 100 feet of net: Number Weight
Rough fish = 15.02 38.93
Game fish = 4.02 8.06
Sunfish = 2.36 0.31
--- Page 17 ---
IIil.
IV.
fish both by weight and number with over 70 percent of the number and
82 percent of the weight contributed by the rough fish. River carp-
sucker (Carpiodes carpio) and smallmouth buffalo (Ictiobus bubalus)
represented over 58 percent of the total catch and averaged 3.9 pounds
and 9.4 pounds respectively.
Although game species comprise a small percentage of the population,
white bass continue to do well, in spite of the rough fish infestation,
contributing almost 9 percent of the total catch in this lake.
Comparisons in the catch per unit effort data (Figure 4) indicates
little change in the overall composition in the past three years other
than an increase in the average weights of the rough fish.
Seining collections were made during June-September on Lake Inks.
Only one young-of-the-year largemouth bass was collected in a total
of 22 seine hauls indicating the possibility of poor reproduction or
survival (Table 8). Only two species of small forage is available and
additional forage such as threadfin shad should be introduced. The
possibility of stocking walleye in this lake should be investigated.
Vegetation has been controlled periodically in Lake Inks by lowering
the lake level during the winter months, thus few vegetation problems
exist at this time.
Public access is limited almost entirely to Inks Lake State Park
facilities but the size of the lake does not warrant additional public
access, There are boat launching facilities within the park area and
bank fishing is possible on over 50 percent of the shoreline.
Significant Deviation:
Plans were made in this segment to conduct cove rotenone surveys on
area lakes where time permitted. The standard procedures to be followed
in the surveys were compiled and distributed late in the segment and
it was felt that it would be best to plan the surveys for the next
segment when better preparations could be made.
Conclusions, Evaluations, and Recommendations;
Canyon Lake will be stocked with additional walleye fingerling and
striped bass in 1974 and 1975. Hopefully, reproducing populations
of both can be established. With the introduction of these species,
additional forage such as threadfin shad should be introduced to pro-
vide more open water forage. Surveys should continue on this lake to
evaluate the walleye and striped bass introductions. Smallmouth bass
might provide an additional sports fish in Lake Canyon and plans should
be made to stock this species when the fish are available.
Lake Travis will be stocked with striped bass again in 1974 and 1975.
Surveys should continue on Lake Travis to assist in the evaluation of
these stockings. Threadfin shad should be introduced in this lake also,
to provide an additional forage species. The possibility of access
improvement in the form of launching facilities should be investigated.
--- Page 18 ---
Species
Notpropis venustus
Gambusia affinis
Menidia beryllina
Dorosoma cepedianum
*Lepomis auritus
*Lepomis macrochirus
*Lepomis megalotis
*Chaenobryttus cyanellus
Percina caprodes
Campostoma anomalum
*Micropterus salmoides
*Micropterus punctulatus
ate
x
Denotes Game Species
~16-
Table 8
Seining Results - Lake Inks
June
(9 hauls)
|
Hor
| YY 3
a 8
i a
' 4 u
8 88
I Ee
' 3 5 0
| 4 an
ns
| 744 . 82.66
2) .22
| 1648 (183.11
2) .22
| 23 2.56
i - i
4) 44
i; 42
fg 1 a2
2 ~~ -,22
Augu
(5 h
st
auls)
Number per
seine haul
5.0
| 7.40
}
an a
September
(8 hauls)
uc
v3
as
a
u u
g 83
& Bed
iS) 3 0
Zz Zo
367 45.88
495 | 61.88
1 »k2
5 62
) | 62
1 -
!
Totals
1136
2180
34
11
NrN re
--- Page 19 ---
Surveys should continue on Lake Lyndon B. Johnson to evaluate the
introduction of walleye and to provide fishery information to the
University of Texas in the evaluation of the thermal effluent on
this lake. There is a need for some type of natural or artificial
cover in Lake Lyndon B. Johnson. Investigations should be con-
ducted as to programs to construct some type of artificial cover
with assistance from local clubs and fishermen. Threadfin shad should
be introduced into Lake Lyndon B. Johnson also.
Although data indicates a high rough fish population in Lake Inks,
no recommendations will be made this year. The evaluation of walleye
introductions in Lake Lyndon B. Johnson will provide valuable infor-
mation as to the feasibility of establishing this species in Lake
Inks to provide an additional sports fish.
The use of monofilament gill nets during the striped bass evaluations
brought about some interesting observations concerning the differences
in the number of game fish caught in the monofilament nets as compared
to those caught in the nylon experimental gill nets used in quarterly
surveys. The monofilament nets were constructed of 150 feet sections
of 3/4, 1-1/4, and 2 inch mesh with the net totaling 450 feet in length.
Although the mesh sizes do not compare with those of the experimental
gill nets, it is felt that the difference is of enough significance to
mention in this report.
It was observed during the netting surveys on Lakes Canyon and Travis
that more game fish were being caught in the monofilament nets being
used in striped bass evaluations than the nylon nets used in quarterly
surveys. The data was compiled in catch per unit effort and the com-
parison is listed below. Due to the different mesh sizes, no other
comparisons could be made. The total fish collected in the three months
of striper surveys were compared with the fall and winter collections
with nylon nets on Canyon and Travis Lakes.
Lake Travis #Rough Fish #Game Fish*
Monofilament Gill nets 7.70/100 ft. net 10.77/100 ft. net
Nylon Gill nets 6.05/100 ft. net 3.01/100 £t. net
Lake Canyon #Rough Fish #Game Fish*
Monofilament Gill nets 11.68/100 ft. net 10.25/100 ft. net
Nylon Gill nets 7.38/100 ft. net 2.64/100 ft. net
*Excludes sunfish
--- Page 20 ---
-18-
Gill Netting Results
Species Checklist
Lyndon B.
Species Inks | Canyon _ Travis Johnson
Lepisosteus osseus
Dorosoma cepedianum
Notemigonus crysoleucas
Cyprinus carpio
Carpiodes carpio
Ictiobus bubalus
Moxostoma congestum
Ictalurus furcatus
Ictalurus melas
Ictalurus natalis
Ictalurus punctatus
Pylodictus olivaris
Morone chrysops
Lepomis auritus
Lepomis macrochirus
Lepomis megalotis
Lepomis microlophus
Chaenobryttus cyanellus
Chaenobryttus gulosus
Micropterus punctulatus
Micropterus salmoides
Pomoxis annularis
Pomoxis nigromaculatis Xx
Cichlasoma cyanoguttatum X
Aplodinotus grunniens
Stizostedion vitreum X
mM mK XK OX
m<
x xX
a
MxM MX OX PS PS OP PS OX
PS Ps PS PS OP OP OX ~< Pm Pd PS PS
PS PS OM OO OS OO OK OM
x PX
mM x OM
x P<
--- Page 21 ---
=1 9
Seining Results
Species Checklist
Lyndon B.
Species _ Inks Canyon Travis Johnson
Notropis amabilis
Notropis venustus x
Notropis lutrensis
Pimephales vigilax
Campostoma anomalum
Percina caprodes
Gambusia affinis
Menidia beryllina
Notemigonus crysoleucas
Dorosoma cepedianum
Etheostoma sp.
Lepomis auritus
Lepomis macrochirus
Lepomis microlophus
Lepomis megalotis xX
Chaenobryttus cyanellus xX
Chaenobryttus gulosus
Carpiodes carpio
Cyprinus carpio
Micropterus salmoides xX
Micropterus punctulatus x
Pomoxis annularis
Ictalurus punctatus
Morone saxitilis
Stizostedion vitreum xX
Cichlasoma cyanoguttatum xX
X
Xx
X
PPS PM OX
PS PS PM PS PS OD OPS OP
P<
ba rm Pd
x
Pal
mx P<
mM Pd Pd PX PX
PPS PS PS PS OP OD DK OK OOK DX
mM PS PS PS PX
ta
a
P< PS PS
mx
x P< PX
--- Page 22 ---
-20-
The monofilament gill nets produced over three times the number of
game fish than the nylon nets in both instances and increased the
rough fish catch considerably in Canyon Lake.
A total of 74 largemouth bass were collected in 4,050 feet of mono-
filament net on Lake Travis while only 82 were collected in over 14,000
feet of nylon net. The number of largemouth bass collected in Canyon
Lake with monofilament net was three times that collected in quarterly
surveys using nylon net.
This illustrates the need for a standard procedure using a variety
of collection techniques to gather management data. The rotenone
samples planned for next segment and the management evaluation tech-
niques presently being designed by department personnel should provide
basis for the collection of more useful data in the future.
Prepared by: D. Wade Butler
Project Leader
Date: March 11, 1974 ___Elgin M. C. Dietz
Region 5-B Inland Fisheries Director
! é
oe
Approved by if tiny.
Dingell-Johnson Coordinator