TPWD 1958 F-2-R-5 #422: Resurvey of the Waters of Region 6-B
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FLE
\ JOB COMPLETION REPORT
Investigations Project
State of TEXAS
Project No. FeR5 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: July 1, 1957 through January 31, 1958
ABSTRACT ;
The year 1957 was one of severe flooding on many of the waters of Central Texas.
For this reason it was deemed desirable to determine the status of the fish populations
of several of the major streams and lakes previously studied under Project F-2-R.
The waters resurveyed were Lakes Inks and Travis and the Lampasas, San Gabriel
and San Saba Rivers.
In all cases it was found that flooding had to some degree affected the fish pop-
ulations of the waters studied. In Lake Inks, young-of-the-year largemouth bass were
found to be quite scarce but young white bass and channel catfish appear to be quite
abundant. In Lake Travis, young largemouth bass are more abundant than they have been
in years, also the result of the flooding.
Stream populations, though undoubtedly affected by flooding, were recovering and
expanding fairly rapidly. The dominant species of previous survey work remained the
»@Ominant species in the 1957 resurveys.
Some items of interest are the appearance of the banded tetra, Astayanax fasciatus
in the Lampasas River, the appearance of the yellowbreast sunfish, Lepomis auritus, in
the San Gabriel River (undoubtedly the result of state fish hatchery stocking) and the
drastic reduction in the abundance of longear sunfish, Lepomis megalotis, in the San
Gabriel River. The gizzard shad, Dorosoma cepedianum, which was quite abundant in the
upper San Saba River apparently was adversly affected by turbid flood waters and is
now quite scarce.
It is recommended that extensive numbers of largemouth bass fry be stocked in Lake
Inks to offset the apparent destruction of the spawn of the species’in 1957.
All told, however, the flooding in 1957 of the waters resurveyed by project personnel
had no serious detrimental effect on the fish populations contained therein although
some habitat destruction due to scouring did occur.
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2.
OBJECTIVES :
To determine the present status of waters and fish populations which have been
previously surveyed in Project F-2-R.
PROCEDURE:
Collections of fish samples were obtained principally through the use of small
meshed seines and standard, experimental type, gill nets. The experimental gill net
consists of five sections of mesh sizes ranging from one-inch square mesh to three
inches square mesh in one-half inch intervals. Each section of webbing is twenty-five
feet long and eight feet deep.
With the exception of the work done on Lake Inks, all seine and net collections
were taken at random, from various habitats. Seine and net collections of fish specimens
from Lake Inks were obtained from long established collection stations.
Seined specimens were preserved, as usual, in ten percent formalin solution and
taken to the regional fishery laboratory for identification and counting.
Gill netted specimens were identified, weighed, measured and examined for stage of
sexual development in the field. These data were recorded on standard data sheets and
later consolidated.
The waters worked by resurvey crews included Lakes Inks and Travis and the Lampasas,
San Gabriel and San Saba Rivers.
DISCUSSIONS AND FINDINGS:
Lake Inks
In August, 1957 a field trip was made to Lake Inks for the purpose of obtaining
data on the present status of the fish population, and to inspect the lake for regrowth
of submergent and emergent vegetation. Seine and net collections of fish specimens were
obtained from the collection stations used during the initial survey.
A second collecting trip was made to Inks Lake during December, 1957 to take seine
samples of shoreline species. The results of all of these collections are presented in
Tables 1 and 2.
It had been rumored by many people that the severe flooding of Inks Lake during 1957
had not only destroyed almost all of the aquatic vegetation but had also destroyed most
of the spawn of the largemouth bass and that the young-of-the-year of this species in
Inks Lake were all but non-existent in the fall of 1957. This was considered a possibility
since 1,282,000 acre feet of water had flooded through the lake during the months of
April and May. In order to check this, seine collections were taken in August and December,
Though the results of the seine collections cannot be considered conclusive, it would
appear that young~-of-the~year largemouth bass were extremely scarce during the time of
the collections. By way of comparison, in August, 1955, 265 seined specimens were col-
lected and of these 17 were largemouth bass fingerlings and yearlings. Similarly, of
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the 30 specimens taken from these same stations in August of 1956, 3 were young large-
mouth bass. However, in August of 1957, only 3 of the 1,122 specimens taken were
young largemouth bass. This seems to indicate that the relative abundance of young of
this species has declined, possibly as a result of the flood of 1957. For this reason
it is considered advisable to stock as many largemouth bass fry as can be obtained
from nearby state and/or federal fish hatcheries during the coming fry stocking season.
Preferably, it would be desirable to stock these fry at the earliest possible date in
order for them to take advantage of the full length of the 1958 growing season.
Net samples of fish taken from Lake Inks during the month of August indicate that
either longnose gar and channel catfish were more numerous than they were in 1955 and
1956, or that they were much more active. Out of 520 fish taken in the eight simultaneous
net sets, longnose gar accounted for 51, or 9.80 percent of the total, and channel cat-
fish accounted for 92, 17.69 percent of the total. Of the total weight of the netted
fish, longnose gar comprised 54.26 percent and channel catfish comprised 15.10 percent.
Reports from camp operators suggest that fishing for catfish and white bass is
better than it has been for a number of years in Inks Lake. This probably is due to
the apparent increase in their relative abundance and the decrease in the total amount
of cover in the lake. This increase in relative abundance is evidenced by the proportion
of the total netted fish in the August net sample composed of channel catfish.
Overall it appears as if the ratio of predator fish to forage and rough fish is
relatively well balanced at this time. Predators, including gars, catfish, white bass,
crappie, sunfishes, and drum comprised approximately 47 percent of the total number of
fish netted in the August, 1957 collections. Forage and rough fish combined and includ-
ing gizzard shad, smallmouth buffalo, river carpsuckers, and carp accounted for the other
53 percent. By weight, the ratio is very much more in favor of the predator species,
77 percent being predators and only 23 percent being forage and rough fish species.
Essentially it can be said that the fish population in Inks Lake at the present time
appears to be in excellent condition. The only apparent exception to this assumption |
seems to be in the searcity of young largemouth bass. This can probably be overcome
with wholesale stocking of bass fry during the 1958 stocking season.
Lake Travis
Lake Travis was subjected to a severe water level fluctuation of some 35 feet during
1957. Heavy spring rains brought the water level from an elevation of 670 feet above
sea-level to a record level of 707 feet. The fluctuation occurred during spring and
early summer and coincided with the spawning season of many fish species in Lake Travis.
Apparently the rising water level was not detrimental to game fish spawn since large
numbers of young game fish were taken in specimen collections by Game and Fish Commission
personnel during the summer and fall of 1957. In addition, anglers on Lake Travis
caught untold numbers of young largemouth black and white bass during the same period.
Twelve seine collections and eighteen gill net collections were made at random dur-
ing the resurvey. A total of 4,430 individuals were taken in seines and 441 in the net
collections. The results of these collections are given in Tables 3 and 1.
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The gizzard shad was the most abundant species taken in the seine collections
accounting for 84.06 percent of total numbers. The largemouth black bass made up
12.40 percent of the total and was the second most abundant. All other species in-
cluding sunfish and the Cyprinids or minnows and shiners, accounted for Less than 4
percent of the total seine collections.
In the netting collec+itons rough fi~’ dominated the collections, making up 59.26
percent of total netted specimens and 71.54 percent of the total weight.
The white bass was the most abundant game fish taken in the net collections with
19.73 percent of the total number taken and 12.49 percent of the total weight.
Throughout 1956 Lake Travis was clear and relatively infertile. However, during
the resurvey period the lake had a desirable bioom of unicellular algae and had changed
from a sterile clear color to a rich, fertile green color.
With the increased fertility and excellent 1957 spawn of game fish species, fishing
should be above average during 1958.
Lampasas River
Because of flooding conditions during the spring of 1957, it was considered advisable
to recheck 4 number of stations on the Lampasas River to see what effect flood waters
had had on the fish population in this stream. For this purpose a field trip was made
to four stations on the Lampasas during September. The results of the seining collections
are presented in Tabie 5.
It was found that, regardiess of the tremendous amount of flood water which passed
through the Lampasas River, the dominant, or rather most abundant, species found in
1953 were again the most abundant species in 1957. However, only i9 of the 32 species
found in 1953 were collected in 1957. This is probably accounted for in the fact that
the very limited study made in 1957 could rot possibly produce the same thorough results
obtained in the earlier study but was intended only to discover any drastic changes
which might have occurred as a result of the flood.
Perhaps the most interesting discovery resulting from the 1957 study was the appear-
ance of the banded tetra, Astayanax fasciatus, in the Lampasas River. This sub-tropical
species has, so far as is known, not been reported from this stream prior to this
writing.
Field observations of young channel catfish indicate an increase in this species in
the river. Similarly, largemouth bass were seen in greater numbers than they were
collected and it appears as if this species as well as the catfish were not too drastic-
ally reduced in numbers by the flood waters. It is recommended, however, that substantial
numbers of both these species be stocked at various places in the river to help in the
rebuilding of good sport fishery in the Lampasas River.
San Gabriel River
The San Gabriel River, like the l[iampasas, suffered from extremely heavy flooding
during the spring of 1957. Because of this it was felt necessary to determine how
seriously the fish population had been affected. For this reason a number of the origins’
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survey collection stations were revisited and seine collections of fish specimens were
obtained. The results of these collections are presented in Table 6.
The stations revisited during the summer of 1957 were primarily in Williamson County,
the portion of the stream which was most seriously flooded.
The most significant difference between the earlier collections made in 1953 and
those made in 1957 was the drastic reduction in the relative abundance of longear sun-
fish, Lepomis megalotis. This species dropped from 22 percent of the specimens collected
in 1953 to only 0.05 percent of those taken in 1957. This would appear to indicate
that the longear sunfish was seriously affected by flooding conditions. Similarly the
central stoneroller, Campostoma anomalum, appears to have been drastically reduced in
relative abundance. In the 1953 collections they comprised 14 percent of the total
specimens whereas they composed only 0.19 percent of the 1957 collection.
Conversely, the yellowbreast sunfish, Lepomis auritus, which was not collected in
1953 comprised 3.55 percent of the specimens taken in 1957. These specimens were un-
doubtedly planted by state fish hatchery personnel.
A species which one would have expected to have been very seriously affected by flood-
ing conditions is the orangethroat darter, Etheostoma spectabile. However, this fish
species remains present in relatively large numbers.
The two dominant notropid species remain, as would be expected, the redhorse shiner,
Notropis lutrensis, and the spottail shiner, Notropis venustus.
San Saba River
Five stations on the upper San Saba River in Menard and Schleicher Counties were
checked with seines in an effort to determine the effects of severe spring flooding on
the fish population. The seine collections were made in November, 1957, at which time
the volume of flow was only slightly greater than during the 1956-1957 survey period.
(Job B-17, Project F-2-R-4). The results of the seine collection are given in Table 7.
Submerged aquatic vegetation including Chara sp., Myriophyllum sp., and Potomogeton
Sp. was sparse in the headwaters of the river, evidently reduced appreciably by swift
waters and high turbidity.
The most abundant fish species found in the seine collection was the spottail shiner,
making up over 63 percent of the total numbers taken. The redhorse shiner and the
parrot minnow were second in abundance, each accounting for 11 percent of the total.
Sunfish, including the redear, longear, green, and bluegill comprised 9 percent of
the total numbers and were the only game species taken in the collections.
Although too few collections were made for accurate comparison with the previous
extended inventory, it appears that the fish population is substantially the same as
found during the initial survey.
The only noticeable exception was the absence of gizzard shad in the collections.
Although taken in large numbers from every station on the upper San Saba River during
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the 1956-57 inventory, ‘this species was not taken in any collection during the resurvey.
High turbidity and radical temperature changes as a result of the heavy rains may have
caused heavy mortality to this susceptible species.
Prepared by: Kenneth C. Jurgens Approved by: ero Ly pote
Project Leader and Chief Aquatic Biologist
John E. Tilton
Assistant Project Leader
Date; April 25, 1958
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Table 1. Lake Inks Seining Results, 1957.
COMMON NAME
Gizzard shad
River carpsucker
Spottail shiner
Redhorse shiner
Parrot minnow
Blackstripe topminnow
Common mosquitofish
Largemouth black bass
Redear sunfish
Bluegill sunfish
lYellowbelly sunfish
Logperch
OTALS
SCIENTIFIC NAME
Dorosoma cepedianum
Carpiodes carpio
Notropis venustus
Notropis lutrensis
Pimephales vigilax
Fundulus notatus
Gambusia affinis
Micropterus salmoides
Lepomis miecrolophus
Lepomis
Lepomis
Percina
macrochirus
auritus
caprodes
DEC. 3
NUMBER
PER CENT
OF NUMBER
47.35
0.07
39.45
5.02
0.89
0.27
0.48
0.21
1.38
4.19
0.34
0.35
100.00
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Table 2. Lake Inks Netting Results, August 19-20, 1957.
COMMON NAME
Gar
Gizzard shad
Smallmouth buffalo
River carpsucker
Carp
Channel catfish
Yellow catfish
White bass
Warmouth
Redear sunfish
Bluegill sunfish
White crappie
Freshwater drum
TOTALS
NUMBER
PER CENT OF NUMBER
PER CENT OF WEIGHT
54.26
4.90
. 243558
3-91
0.90
15.10
1.90
- 3.67
0.03
0.05
0.80
0.77
0.13
100.00
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Table 3. Lake Travis Seining
COMMON NAME
Gizzard shad
River carpsucker
Spottail shiner
Redhorse shiner
Common Mosquitofish
White bass
Texas spotted bass
Largemouth black bass
Redear sunfish
Bluegill sunfish
Longear sunfish
White crappie
Logperch
Rio Grande perch
TOTALS
Results, 1957.
SCIENTIFIC NAME
Dorosoma cepedianum
Carpiodes carpio
Notropis venustus
Notropis lutrensis
Gambusia affinis
Roccus chrysops
Micropterus treculi
Micropterus salmoides
Lepomis microlophus
Lepomis macrochirus
Lepomis megalotis
Pomoxis annularis
Percina caprodes
Cichlasoma cyanoguttatum
CYPRESS CREEK
NUMBER
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Table 4. Lake Travis Netting Results, 1957.
COMMON NAME
Longnose gar
Gizzard shad
‘Smallmouth buffalo
River carpsucker
Grey redhorse sucker
Carp
Blue catfish
Channel catfish
Yellow catfish
White bass
Texas spotted bass
Largemouth black bass
Green sunfish
Bluegill sunfish
Longear sunfish
White crappie
Freshwater drum
Rio Grande perch
TOTALS
HURST CREEK : CYPRESS CREEK PERC
0. _ WE. LBS. | NO. WI. LBS. Oe. No.
4.76]
14.51
2.27
28.34
1.59
3.85
0.23
9.30
0.68
19.73
0.68
4.76
0.22
2.27
0.23
2.72
2.95
0.99
100.00
ENT
Wr.
7.68
7-59
2.10
43.32
1.98
7.38
1.56
7.94
1.77
13.49
0.19
1.85
0.02
0.21
0.01
1.32
1.14
0.45
100.00
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Table 5.
COMMON NAME
Longnose gar
Gizzard shad
Banded tetra
River carpsucker
Spottail shiner
Redhorse shiner
Mimic shiner
Parrot minnow
Stoneroller
Channel catfish
Yellow bullhead
Yellow catfish
Tadpole madtom
Common mosquitofish
Largemouth black bass
Green sunfish
Yellowbelly sunfish
Longear sunfish
Orangethroated darter
TOTALS
Lampasas River Seining Results, 1957.
STATION
NO. 9
SCIENTIFIC NAME Number
Lepisosteus osseus 2
Dorosoma cepedianum --
Astayanax fasciatus
Carpiodes carpio
Notropis venustus
Notropis lutrensis
Notropis volucellus
Pimephales vigilax
Campostoma anomalum
Ictalurus punctatus
Ictalurus natalis
Pylodictus olivaris
Schilbeodes gyrinus
Gambusia affinis
Micropterus salmoides
Lepomis cyanellus
Lepomis auritus
Lepomis megalotis
Etheostoma spectabile
ll.
STATION | STATION STATION
NO. 12 )NO. 15 NO. 17
Number
0.19
0.06
0.13
0.26
34.22
16.46
2.19
37.58
0.06
0.52
0.06
0.06
0.06
2.14
0.06
0.13
1.36
4.00
0.46
100.00
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12. :
Table 6. San Gabriel River Seining Results, 1957.
COMMON NAME
River carpsucker
Weed shiner
Spottail shiner
Redhorse shiner
Parrot minnow
Stoneroller
Channel catfish
Gambusia
Kentucky spotted bass
Green sunfish
Bluegill sunfish
Yellowbelly sunfish
Longear sunfish
Orangethroat darter
TOTALS
SCIENTIFIC NAME
Carpiodes carpio
Notropis roseus
Notropis venustus
Notropis lutrensis
Pimephales vigilax
Gunmcatene anomalum
Ictalurus punctatus
Gambusia affinis
Micropterus punctulatus
Lepomis cyanellus
Lepomis macrochirus
Lepomis auritus
Lepomis megalotis
Etheostoma spectabile
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13.
Table 7. San Saba River Seining Collection, November 19, 1957.
COMMON NAME SCIENTIFIC NAME
River carpsucker Carpiodes carpio
Golden shiner Notemigonus crysoleucas
Spottail shiner Notropis venustus
Redhorse shiner Notropis lutrensis
Mimic shiner Notropis volucellus
Texas shiner Notropis amabilis
Parrot minnow Pimephales vigilax
Gambusia Gambusia affinis
Green sunfish Lepomis cyanellus
Redear sunfish Lepomis microlophus
Bluegill sunfish Lepomis macrochirus
Longear sunfish Lepomis megalotis
Logperch Percina caprodes
Greenthroat darter Etheostoma lepidum
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Figure 5. A wall of water at least six
feet high surges over Inks Lake Dam, April 26,
1957.
Figure 6, Many of the fish which entered
Lake Inks were killed in transit down the rocky
Spillway Creek from Buchanan Dam,
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Figure 7, Test net showed large numbers of
Gizzard shad had reentered Inks Lake during the
height of the flooding.