TPWD 1975 F-2-R-22 #1658: Performance Report: Region V-B Fisheries Studies, Federal Aid Project F-2-R-22
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PERFORMANCE REPORT
As required by
FEDERAL AID IN FISHERIES RESTORATION ACT
TEXAS
Federal Aid Project F-2-R-22
Region V-B Fisheries Studies
Objective B-26: Fisheries Management Recommendations
Project Leader: D. Wade Butler
Clayton T. Garrison
Executive Director
Texas Parks and Wildlife Department
Austin, Texas
Lonnie J. Peters Robert J. Kemp
Chief, Inland Fisheries Director of Fisheries
November 18, 1974
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PERFORMANCE REPORT
State: Texas Project Number: F-2-R-22
Project Title: Region V-B Fisheries Studies
Project Section: Research and Surveys
Study Title: Fisheries Management Recommendations _
Contract Period: February 1, 1974 to December 31, 1974
Program Narrative Objective Number: B-26
ABSTRACT
This objective is designed to situate management practices in the public
waters of Region V-B. To determine management needs, Lakes Canyon, Travis,
Lyndon B. Johnson and Inks were surveyed (gill netting, seining, water quality).
Cove rotenone samples were collected from Lakes Canyon and Lyndon B. Johnson.
Surveys indicate acceptable game fish populations in the lakes surveyed but
all lakes have overpopulations of rough fishes. Recommendations for the lakes
surveyed include continued predator stockings for control of rough fish popu-
lations, habitat improvement to concentrate predators for harvest, and the
construction of fishing piers for additional fishermen access at all times of
the year.
Additional walleye stockings were carried out on’ Lakes Canyon and Lyndon
B. Johnson. Surveys indicate good survival and growth of walleye in both
lakes.
Striped bass were stocked for the second year in Lakes Canyon and Travis.
Survival from both stockings has been documented and growth is excellent in
both lakes. Smallmouth bass were also stocked in Canyon Lake and a portion
of the Guadalupe River near Kerrville, Kerr County.
Northern pike were introduced into Inks Lake and Town Lake.
Objective: To situate fishery management practices in the public waters of
Region V-B.
Te Segment Objectives:
1. To prepare fish harvest regulations for the waters of Region V-B.
2. To recommend management practices for waters not providing adequate
sports fishing.
3. To determine the needs for supplemental stocking of hatchery reared
fish.
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4. To conduct detailed surveys on Lakes Canyon, LBJ, and Travis.
5. To determine the source and extent of natural or artificial
pollutants affecting fish populations.
6. To determine needs for vegetation control.
7. To determine public access.
IL. Summary of Progress:
Meetings were held with game management officers, biologists, and
supervisory personnel. to discuss existing and proposed fishing regula-
tions in the Edwards Plateau, Possum Kingdom, and Trinity-Brazos
Regulatory Districts. Public hearings were also held in each of the
counties under regulatory authority and the proposed proclamation was
presented to the Texas Parks and Wildlife Department Commission for
approval.
Detailed surveys (gill, netting, seining, water quality) were con-
ducted on Lakes Canyon, Travis, Lyndon B. Johnson, and Inks to de-
termine management needs and evaluate stockings. Cove rotenone sur-
veys were also carried out on Lakes Canyon and Lyndon B. Johnson to
estimate standing crops of existing fish populations. Visual surveys
were made on the lakes of the region for vegetation control needs and
public access,
There were no reports of pollution affecting fish populations in
Region V-B this segment.
III. Significant Deviation:
Changes in Department alignment have made it necessary to transfer this
objective to Project F-30-R, Statewide Management, beginning January 1,
1975. Since a report on the progress of this objective was necessary
to affect the change in alignment, the quarterly surveys for the last
quarter were not accomplished and the data reflects only the information
collected for the first three quarters.
IV. Conclusions, Evaluations, and Recommendations:
LAKE TRAVIS
Lake Travis is the second largest lake in Region V-B having a surface
area of 18,930 acres. It is a deep lake (mean depth - 62 feet) im-
pounded upon a limestone basin within the Edwards Plateau, Travis
County. The lake was impounded in 1940 and is utilized for recreation,
flood control, hydroelectric power, and municipal and industrial water
supplies. Lake Travis impounds waters of the Colorado River and is
controlled by the Lower Colorado River Authority.
An additional 137,500 striped bass fingerling were stocked in Lake Travis
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in June, 1974, This was the second year of stocking, bringing the total
stocking to 343,648 stripers over the past two years.
Lake Travis was surveyed quarterly using 150-foot experimental gill nets
set overnight on the bottom at 15 stations. A total of 45 net-nights
produced 845 fish weighing 1,357.26 pounds representing 21 different
species. Game fishes represented 25.09 percent of the catch by number
and 25.84 percent by weight (Table 1). Figure 1 illustrates a three
year trend of rough fish, game fish, and sunfish based on the catch
per 100 feet of net.
The gill netting data reflects overpopulations of gizzard shad (35.86
percent by number, 15.29 percent by weight), river carpsucker, and
European carp. Populations of channel catfish, flathead catfish, and
blue catfish seem to be acceptable as are the populations of largemouth
bass, spotted bass, white crappie, and white bass.
Seine samples were collected only in July and September. Results in-
dicate available forage consisting of predominantly blacktail shiners,
and Mississippi silversides (Table 2). Only four largemouth bass were
collected in seining collections but the morphometry of the basin makes
seining very difficult and the results could be misleading.
Time did not permit cove rotenone surveys on Lake Travis as planned
but the surveys will be carried out during the next segment to determine
Standing crop estimates.
Although few striped bass were collected in netting surveys this segment
there have been numerous reports of catches by area fishermen. September
Striper surveys produced only one from 1974 stockings.
Management Recommendations:
1. The stocking of striped bass should continue. This species could
assistg in the control of the large population of gizzard shad and
other open water rough fishes.
2. Additional forage should be provided for the predator species in
Lake Travis. A few threadfin shad have been collected but additional
stockings of this species should be made in an attempt to establish
a good population in all parts of the lake.
3. The construction of lighted and heated fishing docks could provide
an increase in angler harvest of exotic stockings and native species.
The lake area is heavily populated but only a few areas provide
access to fishermen without the aid of a boat.
4. Brush shelters and baited areas could also be useful in increasing
angler harvest. Such areas could be marked and located in and
around fishing docks to attract fish for harvest.
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Table 1
Results of Lake Travis Gill Netting for 197)
hS Net Sets
Percent Percent
Species Numb er of Weight of average
Number (pounds ) Weight Weight
Lepisosteus osseus 37 4.38 133.01 9.80 3.59
Dorosoma cepedianum 303 35 86 207 .51 15.29 68
Ictiobus bubalus 26 ae 235.50 a er
Carpiodes carpio 7 8.9 190.19 eO1 2.50
Moxostoma congestum 22 2.60 3.238 2.53 1.56
Cyprinus carpio L6 5 luk 142.69 10.51 3.10
Aplodinotus grunniens 15 1.78 42.25 Bakke 2.82
Ictalurus punctatus ho 4.73 37.32 2.75 093
Ictalurus furcatus 15 1.78 62.32 4.59 4.15
Pylodictus olivaris 17 2.00 109 .6h, 8.08 6.45
Morone chrysops 69 8.17 88 by 6.53 1.28
Morone saeettits 1 12 Lb sbd 1.ub
Lepomis macrochirus 56 6.63 12.25 290 22
Lepomis auritus LL 1.30 2.13 016 019
Lepomis megalotis 10 1,18 1.63 112 016
Chaenobryttus cyanellus 12 1.2 2.20 016 18
Chaenobryttus gulosus 3 36 056 Oh 019
Micropterus salmoides 2 at ee ee “ee
Micropterus punctulatus 2 3.0 21.62 1.59 83
Pomoxis saaictaris 19 2.25 13.25 098 s70
Cichlasoma cyanoguttat:. 16 1.89 2.31 Pe fy elk
Totals 845 100.00 1357 26 100.00
Percent of catch by: Numb er Weight
Rough fish = 64.02 72.78
Game fish = 25,09 25 8h
Sunfish = 10.89 1.38
Catch per 100 feet of net: Number Weight
Rough fish = 68,01 1.63
Game fish = 3.1 5.16
Sunfish = 1.36 028
* Denotes game fish species
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prises Pounds of rough fish
~ Pounds of game fish
[] Pounds of sunfish
7 Sa Number
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LAKE CANYON
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LAKE TRAVIS
Figure 1 Three year trend of fish populations in Lakes Canyon and Travis
based on catch per unit effort of netting surveys.
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Seining wesults - Laxe Travis
July septemoer
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orosoma cepvedianun i oel3 a JeL3
Lorosoma petenense - - 3 3636
wobropis verustus 13 1.63 65 &.13
jotropis lutrensis & — 0613 - -
bevonis macrochirus te) 1.06 10 Lees
uBOONLS aur ous - = il ee DU
NOtemigonus crysoleucus 1 Uet3 3 ore
ueiicia very Llina 31 3.83 10 1.25
varpivdes carpio - - 3 Delo
ausenOery hous tus gulosus - - 1 Del3
lag gnales vigilax - - 7 6,88
a chiasoia cyano, uttata - - 3 038
dicropterus sulsoides - - h O50
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venuotes sane Species
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LAKE CANYON
Lake Canyon is a large (8,240 acres), deep (mean depth - 47 feet)
reservoir located entirely within Comal County. The lake was con-
structed in 1964 by the U.S. Army Corps of Engineers and impounds
waters from the Guadalupe River,
Canyon Lake was the target of considerable exotic stockings during this
segment. A total of 16,160 striped bass fingerling were stocked for
the second year bringing the total to 35,910 since June, 1973, Walleye
were also stocked for the second year of a three year schedule. A total
of 124,000 fingerling walie, ere stocked in April and May, 1974. This
brings the total walleye d for 1973-74 to 749,000 fingerling.
Smallmouth bass were also
segment. Approximately 75,
in the lake,
juced into Canyon Lake in May of this
) fingerling were stocked at five locations
Approximately 600 threadfin shad were collected from Lake Calaveras and
stocked into Canyon Lake in April, 1974 in an attempt to provide additional
forage.
Canyon Lake was netted quarterly during this segment using 150-foot
Standard experimental gill nets set overnight on the bottom at 15 stations,
A total of 60 net-nights produced 1,376 fish weighing 2,052.58 pounds
representing 22 species. Game species represented 15.70 percent of the
catch by number and 26.35 percent by weight (Table 3). The remainder
of the catch was comprised of nine species of rough fishes (67.71 percent
by number and 70.02 percent by weight) and five Species of sunfishes
(16.86 percent by number and 3.63 percent by weight). Figure 1 illustrates
a three year trend of rough, game, and sunfishes based upon catch per
100 feet of net.
Netting data reflects high populations of gizzard shad and grey redhorse
suckers representing almost 60 percent of the total catch by number.
Channel catfish represented the greatest numbers of the game species
collected (9.59 percent) while flathead catfish represented the greatest
biomass (10.86 percent).
Large populations of sunfishes are also reflected in the gill netting
with the redear sunfish representing the greatest biomass of this group.
Seining collections were made at five stations (two drags at each
station) monthly from May through September to determine availability
of forage, survival of walleye and striped bass stockings, and survival
of young-of-the-year native predators. The available forage consists
of blacktail shiners, red shiners, threadfin shad and fathead minnows
(Table 4). Large numbers of sunfish were also collected. Good numbers
of young-of-the-year largemouth were collected in July collections, but
few were collected after this time. It is possible that largemouth bass
could be the victim of considerable predation by the large sunfish
population in Lake Canyon.
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Table 3
Results of Lake Canyon Gill Netting for 197)
60 Net Sets
Percent Percent
Species Number of Weight of Average
Number (pounds) Weight Weight
Lepisosteus osseus 27 1.96 69.38 3.38 2.57
Dorosoma cepedianum 20 30.53 176.14 8.58 oh2
Notemigonus crysoleucas 4 029 282 Ae) 220
Cyprinus carpio 51 3.70 20.26 20.48 8.2h
Carpiodes carpio 8 58 26.32 1.28 3.29
Moxostoma congestum 389 28.28 716 45 34.91 1.84
Morone chrysops 23 1.67 26.70 1.30 1.16
* Ictalurus punctatus 132 9.59 262.51 12.80 1.99
*-Ictalurus furcatus 1 207 17.50 085 17.50
‘Ictalurus natalis 1 007 025 Ol 025
* Pylodictus olivaris 33 2.0 223.00 10.86 6.76
* Micropterus salmoides 2h 1.74 15.82 o77 266
Chaenobryttus gulosus 21 1.53 4.63 22 22
Chaenobryttus cyanellus 13 94 1.88 209 elk
Lepomis macrochirus 76 5.52 10.58 051 olh
Lepomis microlophus 120 8.73 56.94 2.77 oh?
Lepomis auritus 2 015 56 003 028
* Pomoxis annularis 11 280 5.76 028 052
* Stizostedion vitreum 15 1.09 16.20 079 i
Cichlasoma cyanoguttata 3 o22 ol9 2Ol ‘
Tilapia sp. 1 07 63 003 63
Carassius auratus 1 07 206 001 006
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Percent of catch by: Number Weight
Rough fish = 67.71 70.02
Game fish = 15.70 26.35
Sunfish = 16.86 3.63
Catch per 100 feet of net: Number Weight
Rough fish = 10 e 31 15 e 97
Game fish = 2..40 6.01
Sunfish = 2.78 83
SSS stent tbssetessnssunecsteestnevensasecs>
* Denotes game fish species
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Table
@liiiny ceoults - Lake vanyon
May June Ju.
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fotropis venustus 37 3.f 222 J2.é 13 Leo 61 4&1 139 13.9 3Ye
4otropis iutrensis 2 Dee f Oel - - ~ - - 9
~epomis microlophus 23 2.3 2b 2.5 ho Leo j L jek 90
wepotris macrochirus 22 2.2 i8 1.8 18 1.8 ho Oh 16 i.6 ee
Lepomis auritus 1 1.6 ih lu 26 3.6 12 1.2 26 £6 lok
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No walleye or striped bass were collected in seine samples, but sur-
vival was documented in netting collections at a later date. One
smallmouth bass was also collected.
Water quality data was collected monthly at two stations.
Cove rotenone samples were conducted in three coves during the month
of August. Results are tabulated in Figure 2. Total average pounds
per acre was calculated at 233.48 pounds and fish were collected repre-
senting 22 species. This represents only the fish actually collected
and does not reflect adjustments for tagged fish returns. Gizzard
shad (63.30 pounds/acre) and yellowbelly sunfish (53.85 pounds/acre)
represented the greatest biomass in the rotenone samples. Gill netting
results did not reflect this high population of yellowbelly sunfish,
but instead indicated a high populations of redear sunfish. Sunfish
represented 103.68 pounds/acre or 45 percent of the total biomass.
Walleye and striped bass were also collected during the surveys.
Overall survey results indicate an overpopulation of large gizzard
shad and to a lesser degree grey redhorse suckers. Overpopulations
of sunfishes also is a problem and probably has an impact upon the
largemouth bass population due to predation and competition. Rotenone
surveys indicated excellent survival and reproduction of the threadfin
shad stocked in the early spring representing 1.74 pounds/acre. It
is hoped that this species will provide additional forage for largemouth
bass and other predators, There has already been evidence that walleye
are utilizing this species,
Walleye continue to be collected and show good growth rates. A total
of 15 walleye were collected during the quarterly netting surveys. The
largest collected to date is 1 pound 14 ounces measuring over 18 inches
in length, Walleye from the 1973 stocking are ranging from 1 pound to
1 pound 14 ounces. Only a few walleye from the 1974 stockings have been
collected, but it appears that the growth rates will conform closely to
last years stocking. Walleye from the 1973 stocking seem to be maturing
and could reproduce this year, The males will definitely mature but it
remains to be seen if the females will develope as well. Sampling will
continue to monitor gonadal development,
Only one smallmouth bass was collected in seining collections, but a
number were collected in the cove rotenone surveys. At this time,
growth rates appear to be slow but survival is good.
Striped bass appear to have survived well from both stockings. Striper
surveys during October, 1974 produced seven stripers ranging from 1 pound
14 ounces to 2 pounds 9 ounces. Five stripers from the 1974 stocking
were also collected.
Management Recommendations:
1. Striped bass and walleye stockings should continue until natural
reproduction is documented. Large populations of gizzard shad
could possibly be controlled if populations of striped bass in-
crease and walleye could crop sunfish populations.
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Loerosoma Cened
-orosoma petenense
Cyprinus carpio
Tilapia $7,
conge stim
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Stizontedion vitreur
Merone chrysoos
LEONE Crys
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* Based on pounds of fis
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53.85
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2. The reservoir should be stabilized during the spawning of large-
mouth bass. Inundation of shoreline areas immediately after spawn-
ing would provide cover and food for young-of-the-year and increase
survival.
3. Angler harvest could be increased with the construction of lighted
and heated fishing docks. Excellent fisheries exists for catfish
and crappie and increased fishermen utilization would result in the
construction of these facilities. Walleye fishing is usually more
productive at night and this type of facility would provide access
when the waters are cooler and more productive for walleye.
4, The construction of fish shelters and baited areas would also in-
crease angler harvest. These structures could be located in and
around fishing docks and access areas and attract fish for harvest.
LAKE LYNDON B, JOHNSON
Lake LBJ is a large (6,375 acres), shallow (mean depth - 22 feet), lake
located in Burnet and Llano Counties. The lake was constructed in 1951
by the Lower Colorado River Authority and is used for hydroelectric
power, cooling waters for a steam generator plant, recreation, and
municipal and industrial water supplies. The lake lies upon a granite
basin and impounds waters from the Colorado and Llano Rivers. Lake
LBJ was chemically renovated in April of 1971.
Walleye were stocked in Lake LBJ for the second year of a three year
schedule. A total of 1,200,000 fry were stocked in May, 1974 bringing
the total stocked to 7,200,000 since May, 1973.
Lake LBJ was netted quarterly using 150-foot standard gill nets set
overnight on the bottom at 15 stations. A total of 46 net-nights yielded
1,291 fish weighing 1,630.25 pounds representing 22 species (Table 5).
Game fishes represented 15.65 percent of the catch by number and 28.48
percent by weight. The remainder included seven species of rough fishes
(80.46 percent by number, 71.03 percent by weight) and five species of
sunfishes (3.89 percent by number, 149 percent by weight). Figure 3
illustrates a three year trend based upon the catch per unit effort in
gill netting samples.
Seining collections were made May through September to determine forage
availability, spawning success, and survival of walleye stockings.
Available forage consists predominantly of threadfin shad, Mississippi
silversides and blacktail shiners (Table 6). Collections indicate low
survival of largemouth bass young-of-the-year. Threadfin shad have
been present in low numbers for a number of years but this year the
species was collected and observed in large numbers.
Cove rotenone surveys were carried out on Lake LBJ also during September,
1974, Three coves were surveyed averaging 220.96 pounds/acre. Carp,
smallmouth buffalo, and gizzard shad represented the greatest biomass
totalling 175.55 pounds/acre of the fish collected (Figure 4). Largemouth
--- Page 15 ---
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Table 5
Results of Lake LBJ Gill Netting for 197)
L6 Net Sets
Percent Percent
Species Number of Weight of Average
Number (pounds) Weight Weight
Lepisosteus osseus 102 Te90 21.94 1.84 2.37
Dorosoma cepedianum 238 18. 61.02 3.74 226
Cyprinus carpio 91 7.05 152.27 9.3h 1.67
Carpiodes carpio 29h 22.76 32.70 19.93 1.10
Moxostoma congestum 2h 1.86 14.50 89 .60
Ictiobus bubalus 103 7.98 121.70 7 7 1.18
Morone chrysops 81 6.27 100.20 6.15 1.2)
* Ictalurus punctatus 6 3.56 72.26 4.43 1.57
Ictalurus furcatus 1 .08 8.00 hid 8.00
Pylodictus olivaris 62 4.80 259.88 15.9h h.19
* Micropterus salmoides 17 1.32 20.82 1.28 1.22
Micropterus punctulatus 1 .08 38 202 238
Micropterus treculi 1 .08 075 205 075
Chaenobryttus gulosus 5 039 1.75 ell 035
Chaenobryttus cyanellus 5 039 1.00 06 220
Lepomis auritus 2 15 56 .03 .28
Lepomis macrochirus 28 2.17 3.44 e2l 12
Lepomis megalotis 10 77 1.20 207 12
Pomoxis annularis 92 Tel3 75 Ol, 4.60 82
Pomoxis nigromaculatus 1 08 9h 06 9h
Stizostedion vitreum 28 2.17 26.33 161 9h
Aplodinotus grunniens 59 57 11.57 8.68 2.40
Totals 1291 100.00 1630.25 100.00
pe eS een
Percent catch by: Number Weight
Rough fish = 80.16 71.03
Game fish = 15.65 28.18
Sunfish = 3.89 oD
Catch per 100 feet of net: Number Weight
Rough fish = 15.07 16.78
Game fish = 2.93 6.73
Sunfish = wf2 12
rn ne
* Denotes game fish species
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“14a
HHH Pounds of rough fish
Pounds of game fish
Pounds of sunfish
Number
Catch per 100 feet of net
1972 1973 1974
LAKE L.B.J.
Catch per 100 feet of net
1972 1973 1974
LAKE INKS ;
Figure 3 Three year trend of fish populstions in Lakes LBJ and Inks
based on catch per unit effort of netting surveys.
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-15-
Table 6
Seining Results - Lake LBJ
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‘ Pomoxis annularis
1
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* Micropterus punctulatus 1
1
5
May July Sept Totals
Number
Number per
seine haul
Number
Number per
seine haul
Number
Numoer per
seine hauls
Species
_---—ee——e—
Dorosoma cepedianum hl 70
Dorosoma petenense 283 160
Notropis venustus 59 96
Notropis lutrensis 8 13
Notropis volucellus - 1
seaidia beryllina 101 170
Lepomis auritus 12
Lepoini macrochirus 9
Lepomis mezalotis 2
Pimephales vigilax
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Micropterus salmoides
Percina caprodes
Cyprinus carpio
Notemizonus crysoleucas -
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venobes pame species
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--- Page 18 ---
Dorosoma cepedianum
Dorosoma petenense
Cyprinus caprio
Carpiodes carpio
Carassius auratus
Moxostoma congestum
Ictiobus bubalus
ictalurus punctatus
Pylodictus olivaris
ictalurus natalis
Ictalurus melas
Chaenobryttus gulosus
Lepomis auritus
Chaenobryttus cyanellus
Lepomis macrochirus .
Lepomis megalotis
Lepomis microlophus
Micropterus salmoides
Micropterus punctulatus
Pomoxis annularis
Cichlasoma cyanoguttata
Aplodinotus grunniens
Tilapia sp.
-16-
Figure
COVE ROTENONE RESULTS
LAKE L.Bwd.
pounds per acre
10 20 30 40 £50 60 70 80
Ht 8 73
H 18.99
--- Page 19 ---
~L7-
bass contributed 9.86 pounds/acre and white crappie 5.45 pounds/acre,
Water temperatures were low during this survey and only 59 percent
of the tagged fish were returned.
Composite results of all surveys on Lake LBJ indicate heavy rein-
festation of rough fishes since renovation in 1971. Very high popu-
lations of carp (average weight - 1.67 pounds) present the most im-
mediate problem. Few larger carp or smallmouth buffalo have been
collected but it seems inevitable that large individuals of both
species will dominate the reservoir within a few years. As in other
lakes of the area, overpopulations of gizzard shad remain a problem.
Only 17 largemouth bass were collected in gill netting samples and
seining collections indicate what appears to be limited spawning
Success, Cove rotenone surveys, however, relate a population of
9.86 pounds/acre which is comparable to that of Canyon Lake. Lake
LBJ has almost no cover present on the lake bottom and little vegeta-
tion is present in the warmer months of the year. This provides for
little protection for young-of-the-year and, consequently low survival.
It is a possibility that carp and smallmouth buffalo also play a part
in poor spawning success of largemouth bass by destroying nests and
prohibiting egg hatching.
Channel and flathead catfish populations seem to be acceptable and
producing. Flathead catfish have made an excellent recovery since
renovation and represented 4.80 percent of the catch by number and
15.94 percent by weight of the gill net collections.
A good fishery also exists for white crappie in Lake LBJ. This species
represented 7.13 by number of gill net collections and reflected a
standing crop of 5.45 pounds/acre.
Walleye were not collected in the cove rotenone Surveys but 28 were
collected in quarterly surveys. Growth rates of the 1973 stocking
have conformed closely to the walleye in Canyon Lake. No walleye
have been collected from the 1974 stocking but surveys will shortly
be carried out to document survival.
Management Recommendations;
1. Lake LBJ has almost no bottom cover for largemouth bass and little
vegetation is present during the warmer months. Some type of cover
(brush shelters, stake beds, etc.) should be constructed on the Lake
bottom to provide shelter for the largemouth bass and other predators.
These areas should be marked for utilization by anglers.
2. Lake LBJ should be lowered prior to spawning of predators and the
shoreline areas planted with some type of winter grass. Subsequent
raising of the water level after spawning would provide cover and
food for newly hatched fry and should increase young-of-the-year
survival.
3. The stocking of walleye should continue until natural reproduction
is documented.
--- Page 20 ---
-18-
4, An additional predator is needed in Lake LBJ capable of cropping
the gizzard shad and other larger rough fishes in open water.
Striped bass should harvest these species and should be stocked
when the fish are available.
5. Heated and lighted fishing docks should be constructed to in-
crease angler harvest. At the present time there are few areas
accessible to bank fishermen since most of the surrounding property
is privately owned.
LAKE INKS
Lake Inks, located in Burnet and Llano Counties, has a surface area
of 803 acres and a mean depth of 23 feet. The lake was constructed
in 1938 by the Lower Colorado River Authority and impounds waters of
the Colorado River immediately upstream from Lake Lyndon B. Johnson
and downstream from Lake Buchanan. Impounded water is used for recrea-
tion and hydroelectric power.
Lake Inks was stocked with 4,000 northern pike fingerling in April
of 1974, and 4,200 catchable Kamloop trout (6-10 inches) in May. A
total of 1,000 catchable Coho salmon (6-8 inches) were also stocked
in May.
The lake was surveyed quarterly this segment using 150-foot standard
experimental gill nets set overnight on the bottom at ten stations.
A total of 30 net-nights produced 775 fish weighing 1,584.75 pounds
representing 18 species. Game species represented 24.77 percent of
the catch by number and 18.75 percent by weight (Table 7). The re-
mainder of the fish collected was comprised of six species of rough
fishes (61.68 percent by number, 80.48 percent by weight) and six
species of sunfishes (13.55 percent by number, .77 percent by weight).
Figure 3 represents a three year trend of fish populations based on
catch per unit effort of gill nets.
Gill netting results indicate very high populations of gizzard shad,
river carpsucker, and smallmouth buffalo. These species represented
74.39 percent of the catch with river carpsucker having the greatest
biomass.
Despite the extremely high rough fish composition, flathead catfish
and channel catfish were collected with regularity in good numbers.
Largemouth bass and spotted bass were also collected in numbers com-
paring with those of other lakes in the area although seining collections
have indicated low young-of-the-year survival for the past two years.
Seining collections were made in June and July of this segment and
results reflect excellent numbers of available forage (Table 8).
Mississippi silversides and blacktail shiners represented the greatest
numbers but threadfin shad appeared in good numbers also. No large-
mouth bass were collected and only four spotted bass.
Norther pike have not been collected in quarterly surveys since stocking
and there have been no reports from area fishermen.
--- Page 21 ---
sk
ak
Ok Ok Ok
-19-
Table 7
Results of Lake Inks Gill Netting for 197)
30 Net Sets
_ eee
Percent Percent
Species Number of Weight of Average
Number (pounds) Weight Weight
eee
Lepisosteus osseus 15 1.9) 2.19 2.66 2.81
Dorosoma cepedianum 219 28.23 80.75 5.10 037
Cyprinus carpio 9 1.16 38 .32 2.2 4.26
Carpiodes carpio 191 2.65 77.76 8 .88 4.06
Ictiobus bubalus 35 4.52 323.51 20.41 9.2h
Morone chrysops 75 9.68 116.26 73h 1.55
Ictalurus punctatus 56 7.23 h7.20 2.98 8h
Pylodictus olivaris 1h 1.81 81.57 5.15 5.83
Micropterus salmoides 16 2.06 19.87 1.25 1.2)
Micropterus punctulatus 28 3.61 30.56 1.93 1.09
Chaenobryttus gulosus 3 039 075 205 wa5
shaenobryttus cyanellus 18 2.32 2.88 18 «lo
Lepomis macrochirus 66 8.52 5.69 36 209
Lepomis microlophus 5 65 1.37 209 027
Lepomis megalotis 9 1.16 «BL 205 209
Lepomis auritus h 052 63 Oh, 16
Pomoxis annularis 3 039 1.57 10 052
Aplodinotus grunniens 9 1.16 16.06 1.01 1.78
eee
Totals 775 100.00 158h.75 100.00
—_—_— _ eee
Percent of catch by: Number Weight
Rough fish = 61.68 80.48
Game fish = 2h.77 18.75
Sunfish = 13 055 77
Catch per 100 feet of net: Number Weight
Rough fish = 10,62 28 3h
Game fish = ).27 6.60
Sunfish = 2,33 27
eee
Lenotes game fish species
--- Page 22 ---
«20
Table 8
Seining Results - Lake Inxs
Se sseesnsensery
June July Totals
be el hed
oF a5
th by by iy
fp He § &s
5 5 ‘o 5 50
= Za 2 Za
species
Menidia beryllina 756 75.6 36 3.6 792
Notropis venustus 173 1743 58 5.8 231
Notemigonus crysoleucas 15 1.5 - - 15
Lorosoma petenense 26 2.6 - - 26
Lepomis auritus 16 1.6 2h 2 ol ite)
Lepomis macrochirus 5 0.5 8 0.8 13
Lepomis megalotis 1 Ol 10 1.0 11
Chaenobryttus cyanellus 2 02 - - 2
Percina caproJes 2 0.2 - - 2
* uicropterus punctulatus - - h Oy h
* Denotes game species
--- Page 23 ---
VI.
«DI
Kamloop trout and Coho salmon were introduced in the upper portions
of Inks Lake near Buchanan Dam. Hydroelectric generation releases
water from a depth of approximately 80 feet from Buchanan Lake provid-
ing cool water for the upper portion of Inks Lake, Project personnel
collected 25 Kamloop trout three weeks after stocking, but following
attempts were unsuccessful. A fisherman was observed in August that
possessed five trout but this is not documented.
Management Recommendations:
1. Predators should be stocked capable of cropping larger rough fishes.
At this time it ig doubtful that the trend of rough fish dominance
can be controlled unless the reproductive success of smallmouth
buffalo, river carpsucker, and European carp can be reduced,
2. Few areas in Lake Inks have sufficient cover for largemouth bass
habitat. Fish attractors should be constructed and marked to in-
crease angler harvest.
Costs: $30,000
Prepared by: D. Wade Butler
Project Leader
Date: November 18, 1974 Elgin M. C. Dietz
Le
Dingell-Johnson Coordinator
Region V
Approved:
Regional Director for Inland Fisheries,