TPWD 1961 F-2-R-8 #715: Resurvey of the Waters of Region 6-B
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Aug
Report of Fisheries Investigations
Resurvey of the Waters of Region 6-B
by
John E. Tilton
Project Leader
and
Gary Wood
Assistant Project Leader
Dingell-Johnson Project F-2-R-8, Job B-20
February 1, 1960 = January 31, 1961
H. D. Dodgen - Executive Secretary
Texas Game and Fish Commission
Austin, Texas
Marion Toole Kenneth C. Jurgens and William H. Brown
Coordinator Assistant Coordinators
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ABSTRACT
A fisheries resurvey was conducted in Region 6-B to ascertain
major changes in fish populations in the rivers and impoundments
previously surveyed. In addition physical changes which might in-
fluence fisheries management work were noted. Only limited surveys
were made on Lakes Buchanan, Marble Falls, Granite Shoals, and Travis
and the Leon and Colorado Rivers. No significant changes in fish
populations were noted but it was found that these waters continue to
carry a sizable rough fish population, exceeding 70 percent of the
total netted fish.
Lakes Inks and Belton were subjected to heavy netting pressure
and results obtained are considered to be comparable to results of
preceding segments. Rough fish were found to dominate the nettable
population in both total numbers and total weight.
It is believed that certain factors, probably involving commercial
netting, have influenced the rough fish complex on Lake Belton. The
removal of large numbers of smallmouth buffalo in 1958 has presumably
resulted in an increased percentage of carpsucker in the netting collec-
tions as well as an increase in pounds per foot of net for this species.
The large rough fish population found to be present in Inks Lake
has resulted in a project designed to test the effectiveness of physical
removal of these species.
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Segment Completion Report
State of Texas
Project No. F-2-R-8 Name: Fisheries Investigations and Surveys
of the Waters of Region 6-B.
Job No. B-20 Title: Resurvey of the Waters of Region 6-B
Period covered: February 1, 1960 - January 31, 1961.
OBJECTIVES
To determine the present status of waters and fish populations which have been
previously surveyed in Project F-2-R.
PROCEDURE
Fish collections were made principally through the use of small-mesh experimental
gill nets. Small-mesh seine collections were made to check spawning success and forage
fish populations.
One rotenone sample was taken for comparison with the net collections. However,
for reasons later explained, this data is not considered reliable. All specimens
taken in the net collections were weighed, measured and checked in the field for
gonadal development.
Random net sets were used to sample fish populations in all of the waters resur-
veyed except Inks Lake. In Inks Lake netting stations established in 1955 were utilized
during this segment along with some random sets.
Any major physical change which might influence distribution, movement, or
spawning success of the fish population was noted at each of the concerned waters.
Six lakes and one river were surveyed during the segment, but only Lakes Inks
and Belton were worked extensively enough for comparison with previous surveys.
Lakes Granite Shoals, Buchanan, Marble Falls, and Travis were visited, and netting
collections were made in an effort to note major changes in the fish population and
to keep familiar with the waters. No attempt will be made to evaluate the results in
detail or compare them with previous, more extensive surveys.
The Leon River below Belton Dam was surveyed to determine the desirability of a
complete fisheries renovation. Limited resurvey and reconnaissance under Job B-22
will be continued during the coming segment on the waters of Region 6-B, except on
Lake Inks and Buchanan, as noted in the following discussions of those impoundments.
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FINDINGS AND DISCUSSION
Lake Granite Shoals
Two trips were made to Lake Granite Shoals during the segment period, one on
August 4 and 5, and one on November 22 and 23. A total of 24 experimental gill nets
were set during the trips. Results of the collections are presented in Table l.
Rough fish, including longnose gar, gizzard shad, freshwater drum, carp, river
carpsucker, gray redhorse sucker, and smallmouth buffalo made up 72.54 percent of
total numbers taken and 85.57 percent of total weight.
In spite of the number of rough fish, sport fishing has remained good and com-
mercial development of fishing docks and other accomodations is increasing yearly.
Principal game species taken during the year were white crappie, white bass, black
basses and channel catfish. Good catches of white bass and crappie were made through-
out the year, but channel catfish were reportedly taken in far fewer numbers than in
previous years.
Lake Buchanan
A total of 39 experimental gill nets were set in Lake Buchanan during the seg-
ment. Rough fish, including longnose gar, gizzard shad, smallmouth buffalo, river
carpsucker, gray redhorse sucker, carp and freshwater drum accounted for 70.23 per-
cent of total numbers and 81.64 percent of total weight taken in the net collections.
The results of the netting collections are presented in Table 2.
From reports of fishermen and camp operators, sport fishing was fair throughout
the year. A seasonal improvement takes place when white bass move to the head of
the lake to spawn. This concentration occurs in late winter through early spring
and fishing success improves greatly in the upper lake and up the Colorado River for
approximately 40 miles. An extensive resurvey of Lake Buchanan will be accomplished
under Job B-24 during the coming segment.
Lake Marble Falls
Twenty-one gill nets were set on Lake Marble Falls during the segment period.
Rough fish made up 70.85 percent of total numbers and 82.18 percent of total weight
netted. Although the lake maintains a good channel catfish population and seasonally
white bass fishing is good, the lake does not support a heavy sport fishery. Fish
taken per foot of net in Lake Marble Falls was computed at 0.15 as compared with 0.23
in Lake Granite Shoals, located immediately above on the Colorado River. In pounds
of fish per foot of net, Marble Falls produced 0.15 compared with 0.30 in Lake Granite
Shoals. Physiography of the lake basin is believed to be at least partially respon-
sible for the poor fish population. Collection data for Lake Marble Falls is found in
Table 3.
Lake Travis
Two trips were made to Lake Travis but only six gill nets were set. The data
obtained is considered too meager for presentation in this report.
Leon River
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The Leon River was resurveyed primarily to ascertain the desirability of a total
fish eradication and restocking program. The segment of the river surveyed extends
from Belton Dam to a small dam located approximately three miles downstream. Although
the limited fish population present indicates needed renovation, no management work
will be undertaken until such time as the City of Temple approves the project.
Lake Belton
Eighty-four gill nets were set during the segment period. Although all were ran-
dom sets, an attempt was made to obtain lake coverage by netting the upper and lower
lake on the same trip. The results of the net collections are shown in Table 4.
An examination of the data reveals a number of interesting facts, but interpre-
tation is difficult. Changes in the smallmouth buffalo and river carpsucker popula-
tions have been pronounced over the past three years. ,
Species Percent Percent Percent Percent Percent | Percent
of number | of weight of number | of weight of number | of weight
Buffalo 7.85 23.19 2.83 3.73 8.25
Carpsucker 1.94 5.91 6.57 13.52 10.97
i
“3.28
As can be seen, the buffalo population appears in the netting data in far greater
numbers in both the 1958 and the 1960 segments than in the 1959 segment. The reduction
in 1959 is believed to be correlated with the removal of large numbers of smallmouth
buffalo by a commercial fisherman during late 1958 and early 1959.
19.22
In 1958, smallmouth buffalo were taken at the rate of two pounds per 100 feet of
net set. River carpsucker were taken at 0.8 pounds per 100 feet. In 1959, six
months after the commercial fisherman ceased operation, the buffalo population was
found to be considerably reduced. Netting results in 1959 showed a rate of catch for
buffalo at 0.5 pounds per 100 feet of net and river ecarpsucker were taken at one pound
per 100 feet of net. In 1960, river carpsucker were taken at a rate exceeding 2 pounds
per 100 feet of net and smallmouth buffalo at 3 pounds per 100 feet of net.
Although the reason for the 1959 decline in the nettable buffalo population is
not understood, the only known factor which might account for the decline (outside of
sampling error) is commercial fishing. The market price for smallmouth buffalo is
considerably higher than for other rough fish available and therefore they are selece-
tively searched out and taken. During this period the lake was commercially netted
and approximately 40 pounds of buffalo per surface acre were removed. The mesh size
of commercial nets used on Belton Lake were too large to take many river carpsuckers
and this species shows a steady increase in the netting collections from 1958 through
1960.
a
o
Because the indicated buffalo decline is so pronounced, an assumption is made
that there was a reduction in the total buffalo population in Lake Belton. The re«
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whe
duction is at least partially attributed to the effects of commercial fishing. In
support of this assumption is the fact that three other lakes surveyed do not show
great changes in the buffalo-carpsucker complex. Lakes Granite Shoals, Buchanan,
and Inks have rough fish populations in which either buffalo or carpsucker predomi-
nate. None of the three have shown a major change in relative abundance of the two
species.
Of the three lakes referred to in the preceding paragraph, two -- Inks and
Buchanan -- show a predominance of carpsucker over buffalo in the netting collections.
In Lake Granite Shoals the smallmouth buffalo is taken in much higher numbers than the
carpsucker. Two theories have been advanced to explain the difference in this popu-
lation complex. One is the factor of lake age. Lake Granite Shoals, which contains
the highest buffalo population, is the youngest at eight years of age as compared to
23 years each for Lakes Buchanan and Inks. It is possible that lake age may largely
account for the difference in relative abundance of the two species.
Another theory is the possible effect of commercial netting. Lake Granite Shoals,
which maintains the largest buffalo population, has been virtually closed to commer-
cial netters. Lake Buchanan, which has the highest nettable carpsucker population,
has supported almost constant commercial netting. Lake Inks has been netted heavily
at times.
Lake fertility does not appear to be a major factor as the three lakes are ina
continuous chain along the Colorado River. Lake Granite Shoals and Buchanan are
considered somewhat more fertile than Inks Lake because of the influence of major
tributaries.
Lake Belton appears to have the lowest overall fish population among the impound-
ments in Region 6-B. In both fish/100 feet of net and pounds of fish/100 feet of net,
Lake Belton has reflected considerably smaller populations than Lakes Granite Shoals,
Inks, and Buchanan during the past three years. However, game fish populations were
found to be substantially the same in all four lakes. The significance of this is
not understood, although it would appear that Belton Lake is less fertile than those
on the Colorado River drainage, but that for the period which the impoundment has
existed (eight years), game fish have been able to compete successfully with rough
species.
Lake Inks
A total of 107 gill net sets were made during nine months of the segment. Most
were at netting stations established in 1955, although some random sets were made.
Results of the net collections are shown in Table 5.
Results of a total kill attempt utilizing rotenone at 1 p.p.m. in a small cove of
the lake are not included here since high winds apparently carried large quantities
of the toxicant into open water where shad were observed dying several hundred yards
from the area treated. Many fish in the cove itself apparently escaped the lethal
effects of the rotenone.
Rough fish, including longnose gar, smallmouth buffalo, river carpsucker,
European carp, gizzard shad, and freshwater drum comprised 72.21 percent of the num-
bers and 79.07 percent of weight of fish netted. These figures are in line with
past surveys in regard to the rough fish-game fish ratios for the impoundment. The
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following shows comparable figures for the past three segment periods:
Percent rough fish (number)
Percent rough fish (weight)
Gizzard shad accounted for over 41 percent of numbers and 6.5 percent of weight
of fish netted as opposed to just under 38 percent and 5 percent respectively during
1959. The slight increase indicated may be real, but is not significant. It is felt
that the fish population complex that now exists compares closely with that of recent
years.
Due to continued lack of fishing success in Lake Inks as well as its relatively
small area (900 surface acres), Job E-6 was submitted and subsequently approved for
the purpose of removing large quantities of rough species, especially river carpsucker,
longnose gar, and smallmouth buffalo from Lake Inks. In conjunction with this job,
an extensive resurvey under Job B-2 will be continued during the coming segment.
Prepared by John E. Tilton Approved by 01, feb iiapentes Zpote
Project Leader Dire¢tor Inland Fisheries Division
Gary Wood
Assistant Project Leader
Date | April 18, 1961
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6.
Table 1. Lake Granite Shoals netting results, 1960.
: Percent Percent
Species Number of Weight of
number (pounds weight
Longnose gar 3.93
Gizzard shad 3.41
Smallmouth buffalo 50.74
River carpsucker 22.83
Gray redhorse sucker 0.54
Carp 3.28
Channel catfish 7.35
Flathead catfish 0.49
White bass 3.09
Texas spotted bass 0,15
Largemouth bass 0.86
Warmouth 0.02
Green sunfish 0.02
Redear sunfish 0.02
Bluegill 0.54
Orangespotted sunfish 0.03
Longear sunfish 0.06
White crappie Laff
Freshwater drum 0.84
Totals 685 914.50 100.00
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Table 2. Lake Buchanan netting results, 1960.
Species
Longnose gar
Gizzard shad
Smallmouth buffalo
River carpsucker
Gray redhorse sucker
Carp
Channel catfish
Flathead catfish
White bass
Largemouth bass
Green sunfish
Redear sunfish
Bluegill
Longear sunfish
White crappie
Freshwater drum
Totals
Percent | Percent
Number of Weight of
number pounds weight
1.75
0.47
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8.
Table 3. Lake Marble Falls netting results, 1960.
Percent
of
Percent
of Weight
number
Species
Longnose gar
Gizzard shad 16.99
Smallmouth buffalo 25.87
River carpsucker 33.00
Channel catfish 10.22
White bass 3.74
Texas spotted bass 0.23
Largemouth bass 210
Warmouth 0.10
Bluegill 0.14
White crappie 3.95 0.98
| moce | tone
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an A i
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Table 4. Lake Belton netting results, 1960.
Percent Percent
Number of Weight
number pounds ig
Species
Spotted gar
Longnose gar
Gizzard shad
Smallmouth buffalo |
River carpsucker
Gray redhorse sucker
Carp
Channel catfish
Flathead catfish
White bass
Texas spotted bass
Largemouth bass
Warmouth
Green sunfish
Redear sunfish
Bluegill
Longear sunfish
White crappie
Freshwater drum
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Table 5. Lake Inks netting results, 1960.
Percent
Number of Weight
number pounds
Species
' Longnose gar
Gizzard shad
Smallmouth buffalo
River carpsucker
Carp
Channel catfish
Flathead catfish
White bass
Largemouth bass
Warmouth
Green sunfish
Redear sunfish
Bluegill
Longear sunfish
White crappie
Freshwater drum
Totals
596.05
197.32
468.15
1,010.38
93.19
275 +39
141.33
115.42
38.25
8.11
ee al
3.72
8.68
3.03
26.12
2h ok
Percent
of
weight
19.72
6.53
15.49
33.44
3.09
9.12
4.67
3.81
127
0.26
0.08
0.13
0.28
0.12
1.20
0.80
2,490 100.00 | 3,021.89 100.00
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ad
A checklist of species mentioned in report.
Common name
Spotted gar
Longnose gar
Gizzard shad
Smallmouth buffalo
River carpsucker
Gray redhorse shiner
Carp
Channel catfish
Flathead catfish
White bass
Texas spotted (Guadalupe) bass
Largemouth bass
Warmouth
Green sunfish
Redear sunfish
Bluegill
Orangespotted sunfish
Longear sunfish
White crappie
Freshwater drum
ain
Scientific name
Lepisosteus oculatus
L. osseus
Dorosoma cepedianum
Ictiobus bubalus
Carpiodes carpio
Moxostoma congestum
Cyprinus carpio
Ictalurus punctatus
Pylodictus olivaris
Roccus chrysops
Micropterus treculi
M. salmoides
Chaenobryttus coronarius
Lepomis cyanellus
L. microlophus
L. macrochirus
L. humilis
L. megalotis
Pomoxis annularis
Aplodinotus grunniens