TPWD 1971 F-6-R-18 #1424: Fisheries Investigations - Region 5-B: Job No. II Stocking Recommendations, Federal Aid Project No. F-6-R-18
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JOB PROGRESS REPORT
As required by
FEDERAL AiD IN FISHERIES RESTORATION ACT
TEXAS
Federal Aid Project No. F-6-R-18
FISHERIES INVESTIGATIONS - REGION 5-B
Job No. II Stocking Recommendations
Project Leader: Roger L. McCabe
James U. Cross
Executive Director
Texas Parks and Wildlife Department
Austin, Texas
Fred G. Lowman Roy T. Huffman
Branch Head, Inland Fisheries Director, Current Operations
November 11, 1971
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SUMMARY
As in the previous two years, there were no newly constructed or renovated
waters which warranted stocking surveys this segment. Surveys were conducted
at the Frio, Nueces, and San Antonio Rivers and at Corpus Christi and Alice
Lakes.
Species composition, numbers of young game fishes, and/or rough fish to
game fish ratios were considered less than desirable in data from the Frio and
Nueces Rivers. These factors were found to be satisfactory at Corpus Christi
and Alice Lakes, although some game species have indicated declines in numbers.
No fingerling stockings are recommended at this time, but releases of
advanced young channel catfish are planned for Alice Lake at a later date.
Releases of young flathead catfish are recommended at Alice Lake and Lake
Corpus Christi when they become available from Region V hatcheries.
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JOB PROGRESS REPORT
State Texas
Project No, _F-6-R=18 Project Title: Fisheries Investigations -
Region 5~-B
Job No. ) Job Title: Stocking Recommendations
Period Covered: Jasuary 1, 1970 to December 31, 1970 __
Objectives:
To determine the waters in Region 5-B which would benefit from stocking.
1, To recommend stocking ratios for newly constructed or renovated
waters,
N
To determine the species composition and abundance of young fishes in
specified waters having established fish populations.
3, To recommend stocking of specified waters having established fish
populations which exhibit deficits of young game fishes.
Procedures:
As in the previous two years, there were no newly constructed or renovated
public waters which warranted stocking surveys this segment. Surveys were
conducted at the Frio, Nueces, and San Antonio Rivers and at Corpus Christi
and Alice Lakes. Locations and descriptions of the areas sampled are provided
in the job progress report prepared last year (segment 17). Two surveys were
conducted at each of the sites. Additional data were obtained from Lake
Corpus Christi in conjunction with a fish aging study (Job IV) being conducted
there during this period.
Sampling methods consisted of overnight gill netting and marginal seining.
Various numbers of nylon straight mesh and experimental gill nets were employed.
Straight mesh nets consisted of l-, 14-, or 2-inch mesh and were 100 feet long.
Experimental gill nets were constructed of graduated mesh sizes from 1-34 inches
square and were 150 feet long. A 20-foot straight seine having one-fourth of
an inch mesh and a 32-foot bag seine also having one-fourth of an inch mesh
were used to capture young-of~-the-year and other small specimens,
Numbers and bulk weights were determined by species and game fish-rough
fish percentages were calculated. Individual weight and length data were re-
corded for all game fishes and for representative rough fish individuals from
various size groups.
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Procedures: (Con.)
Water analyses were conducted during each survey. Surface samples were
tested for temperature, dissolved oxygen, carbon dioxide, alkalinity, tur-
bidity, pH, chlorides, and total hardness.
Since common names are used in this report, a checklist of all species
encountered is provided in Table 1. This checklist gives the common and
scientific names recognized by the American Fisheries Society as featured
in their Special Publication No. 6, A List of Common and Scientific Names of
Fishes From the United States and Canada (Third Edition).
Findings:
Frio River
(Live Oak County)
Six experimental gill nets were set ina one-mile stretch of the river
near and adjacent to Tips County Park along State Highway 72. Water levels
fluctuate greatly at this site and frequent flooding results in redistribution
of fish populations. Table 2 shows the combined netting results from the
Frio River during June and October. Gars and smallmouth buffalo were the
most numerous species captured and comprised the largest percentages by weight.
Two unusually large alligator gar, one weighing 100 pounds and the other 60
pounds, greatly influenced the per cent by weight of rough fishes. Game
fishes accounted for 33.75 per cent of the 80 individuals caught, while rough
fish species comprised 66.25 per cent of the total. The 1970 game fish-rough
fish ratio was much more favorable than in 1969, when game fishes comprised
only 4.49 per cent of the total yield.
Seining efforts were also more productive than in 1969. Young-of-the-year
channel catfish, largemouth bass, white bass, and white crappie were taken
in relatively good numbers during both of the 1970 surveys. In addition,
red shiners of all age classes were very abundant. Bullhead minnows, thread-
fin shad, Mexican tetra, and tidewater silverside were other forage species
recorded in moderate numbers.
Approximately 2,000 channel catfish fingerlings were released in the Tips
Park area of the river in August. Few of these individuals were in evidence
during the October survey.
Results of the 1970 water analyses are shown in Table 3. A rather high
carbon dioxide reading of 12.0 ppm was recorded during the June 24 survey.
Although this reading is far from lethal when accompanied by a dissolved
oxygen reading of 6.0 ppm, it is worthy to note the marked increase over the
less than 5.0 ppm reading taken during the May 1969 survey. The June pH
reading of 7.1 is somewhat lower than the 8.5 recorded ‘in May 1969. The
increase in carbon dioxide and decrease in pH during the June analysis could
possibly be the result of a high carbonic acid content at the time of sampling.
All other readings were considered normal.
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Table 1
Species Checklist
_Common Name si‘ Scientific Name
Spotted gar Lepisosteus oculatus
Longnose gar Lepisosteus osseus
Alligator gar Lepisosteus spatula
Ladyfish Elops saurus
Gizzard shad Dorosoma " cepedianum
Threadfin shad Dorosoma petenense
Mexican tetra Astyanax mexicanus
Carp Cyprinus carpio
Speckled chub Hybopsis aestivalis
Golden shiner Notemigonus crysoleucas
Blackspot shiner Notropis atrocaudalis
Ghost shiner Notropis buchanani
Pugnose minnow Notropis emiliae
Red shiner Notropis lutrensis
Proserpine shiner Notropis proserpinus
Blacktail shiner Notropis venustus
Bullhead minnow Pimephales vigila vigilax
River carpsucker Carpiodes carpio
Smallmouth buffalo Ictiobus bubalus
Blue catfish Ictalurus furcatus
Black bullhead Ictalurus melas
Yellow bullhead letalurus natalis
Channel catfish Tetalurus punctatus
Flathead catfish Pylodictis olivaris
Atlantic needlefish Strongylura marina
Sheepshead minnow Cyprinodon variegatus
Mosquitofish Gambusia affinis
Sailfin molly Poecilia latipinna
Tidewater silverside Menidia beryllina
White bass Morone chrysops
Green sunfish Lepomis cyanellus
Warmouth Lepomis gulosus
Bluegill Lepomis macrochirus
Longear sunfish Lepomis megalotis
Redear sunfish Lepomis microlophus
Largemouth bass Micropterus salmoides
White crappie , Pomoxis annularis
Black crappie Pomoxis nigromaculatus
Freshwater drum Aplodinotus grunniens
Atlantic croaker Micropogon undulatus
Rio Grande perch Cichlasoma cyanoguttatum
Striped mullet Mugil cephalus
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Table 2
Frio River Netting Results, June and October 1970
yPer Cent | Per Cent |
Alligator gar
Spotted gar
Longnose gar
Smallmouth buffalo
Channel catfish*
Flathead catfish*
Redear sunfish*
Bluegil1l*
White crappie*
Black crappie*
Freshwater drum
AADNOwW PNM OO Ah
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FOOOON ODWEFE OS
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__| 80] 100.00
Game fish
Rough fish
* denotes game fish
Table 3
Frio River Water Analyses Results, 1970
Date: " June 24 October 22
Location: Tips Park Tips Park
Depth: Surface Surface
Water temperature: 80°F
Dissolved oxygen (ppm): 6.0
Carbon dioxide (ppm): 12.0
M. O. alkalinity (ppm): 260.0
Turbidity (secchi):
pH: _
Chlorides (ppm Cl ):
Total hardness (ppm CaCO3) :
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Findings: (Con.)
Nueces River
(Nueces County)
Three experimental gill nets each were set in the Bazemore Park and River
Park vicinities. These areas are also subjected to frequent flooding and popu-
lation fluctuation, Rough fish species normally constitute a very large per-
centage of the total netting yield, as can be seen in Table 4. Saltwater
species such as croaker, striped mullet, and blue crab are frequently encoun-
tered during surveys in the area between Wesley Seale Dam and Nueces Bay.
Rough fish species comprised 92.26 per cent of the total number caught and
95.84 per cent of the total weight as compared to 90.74 per cent by number
and 97.85 per cent by weight in the 1969 sample. lLongnose gar and gizzard
shad jointly accounted for 73.80 per cent of the total number and 55.20 per
cent of the total weight. There were no young-of-the-year game fishes taken
in either of the two gill netting efforts.
Steep banks and swift, deep water characterize the Nueces River at the
two sampling sites. These conditions limit seining activities to only a few
areas, which are less than optimum. There were no young-of-the-year game
species taken by seining and forage fish (pugnose minnow, red shiner, sheeps-
head minnow and sailfin molly) numbers were down considerably from the pre-
vious year. Freshwater shrimp (Palaemontes sp.) were very noticeable, as they
have been for the past several years.
Approximately 4,000 channel catfish fingerlings were released on August 26,
1970, at sampling sites on the Nueces River. As in the Frio River, there
were no individuals representative of this release in the sampling yields,
which suggests very poor survival or relocation of these fish.
Table 5 shows results of the spring and fall water analyses. These
results are very comparable to those of 1969, although the methyl orange
alkalinity readings were down an average of 40 ppm. No detrimental readings
were revealed.
San Antonio River
(Karnes County)
Two experimental and one 14-inch straight mesh gill nets were set during
each survey in a rather isolated area of the San Antonio River known as
Conquista Park, near FM Road 791, Karnes County. The presence of 71 longnose
gar (55.04 per cent of the total number of fishes caught) greatly overbalanced
the netting yield of the June and October samples. This resulted in a decline
in the overall game fish percentages as compared to the previous year's data.
The combined 1970 netting results (Table 6) included data from 12 species,
while only seven species were netted in 1969. Channel catfish comprised the
largest percentage of game fishes captured during 1969 and 1970. The mean
weights from this species for those two years were 1.0 and 1.1 pounds,
respectively. Although several sexually immature channel catfish were noted,
there were no 0-1 age group game fishes taken in gill nets.
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Table 4
Nueces River Netting Results, May and October 1970
“Per Cent _ , ~ Per Cent
Alligator gar
Spotted gar
Longnose gar
Threadfin shad
Gizzard shad
Smallmouth buffalo
Channel catfish*
Blue catfish*
Striped mullet
White bass*
Bluegill*
Black crappie *
Freshwater drum
Croaker
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Table 5
Nueces River Water Analyses Results, 1970
Date: May 14 October 26
Location: Nueces River Park Bazemore Park
Depth: Surface Surface
Water temperature: 77°F
Dissolved oxygen (ppm): 8.0
Carbon dioxide (ppm): 5.0
M. O. alkalinity (ppm): 200.
Turbidity (secchi):
pH: _
Chlorides (ppm Cl ):
Total hardness (ppm CaC0O3):
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Table 6
San Antonio River Netting Results,
June and October, 1970
Per Cent
Wt.
Spotted gar
Longnose gar
Gizzard shad
Smallmouth buffalo
River carpsucker
Channel catfish*
Flathead catfish*
Largemouth bass*
Warmouth*
Longear sunfish*
White crappie*
Rio Grande perch
Or ODOOO DF OUWN
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Game fish
Rough fish
*denotes game fish
Table 7
San Antonio River Water Analyses Results, 1970
Date: June 11 October 19
Location: Conquista Park Conquista Park
Depth: Surface Surface
Water temperature: 78°F 64°F
Dissolved oxygen (ppm): 6.0 6.0
Carbon dioxide (ppm): 12.0 -
M. O. alkalinity (ppm): 280.0 240.0
Turbidity (secchi): 368 mm 363 mm
pH: _ 7.8 7.5
Chlorides (ppm Cl ): 115.0 85.0
Total hardness (ppm CaCO3): 300.0 290.0
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Findings: (Con.)
Seining attempts were very successful in procuring young-of-the year
specimens, particularly channel catfish. Nighttime sampling was very pro-
ductive in a wide stretch of shallow rapids approximately 50 yards long and
in an area directly below these rapids. The fast-moving water necessitated
the use of a shorter straight seine rather than the 32-foot bag seine normally
used. The June survey yielded 52 young-of-the~year channel catfish, and the
October survey captured 20 of these juveniles with relative ease. In addition
to the channel catfish, two juvenile largemouth bass comprised the remainder
of the game fish seining yield. Numerous gizzard shad (616) of all age groups
were also captured. Red shiner, bullhead minnow, and mosquitofish were forage
species found in moderate numbers. A species not normally encountered in
other areas of Region 5=B, the speckled chub, was also recorded during the
October sample.
As shown in Table 7, the San Antonio River water analyses results were
much like those from the Frio River. A relatively high carbon dioxide reading
(12.0 ppm) was recorded during the June survey and was accompanied by a some~
what lower than normal pH reading (7.8). Normally, the carbon dioxide reading
is around 5.0 ppm at midday and pH readings are in the vicinity of 8.5. As
in previous analyses, alkalinity readings were higher than other waters tested
due to the many large limestone outcroppings found in and along the river
basin.
Lake Corpus Christi
(Live Oak, Jim Wells, and San Patricio Counties)
Two experimental and one 14-inch straight mesh gill nets were set overnight
during each of the spring and fall sampling trips to Lake Corpus Christi.
Data from these surveys were supplemented with those from four additional
netting ventures made in conjunction with an experimental aging study (Job IV)
being conducted by F-6-R personnel. Results of the two regular surveys (May
and December) are presented in Table 8. Freshwater drum and spotted gar
exhibited marked increases in the overall netting yield while smallmouth
buffalo and gizzard shad numbers have remained relatively stable. Although
blue and channel catfishes have maintained satisfactory numbers, flathead
catfish were not represented in spring and fall samples. Similarly, large-
mouth bass, white crappie, and black crappie have maintained adequate popu-
lations, but white bass, while not lacking, were not obtained in quantities
experienced previously.
Marginal seining captured limited numbers of O-1 age group largemouth bass
and crappie. Channel and blue catfishes were not taken by this
reproduction OF nee SEE ee umerous juvenile blue-
ei and redear sunfishes were recorded. , Forage species were strongly evident
in all drags, with threadfin shad, Mexican tetra, Rio Grande perch, and pugnose
minnows comprising the majority of the catch.
Water chemistry information is provided in Table 9. Other than lower
alkalinity and pH readings, conditions were much as they were in 1969. No
deleterious readings were disclosed.
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Table 8
Lake Corpus Christi Netting Results,
May and December, 1970
Spotted gar
Gizzard shad
Smallmouth buffalo
Carp
Channel catfish*
Blue catfish*
Yellow bullhead
White bass*
Largemouth bass*
Bluegill*
White crappie *
Black crappie*
Freshwater drum
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Game fish
Rough fish
*denotes game fish
Table 9
Lake Corpus Christi Water Analyses Results, 1970
Date: May 22 December 10
Location: Camp Bell Weber's Camp
Depth: Surface Surface
Water temperature: 65°F
Dissolved oxygen (ppm): 8.0
Carbon dioxide (ppm): 8.0
M. O. alkalinity (ppm): 170.0
Turbidity (secchi): 370 mm
pH: _ 7.8
Chlorides (ppm Cl ): 47.5
Total hardness (ppm CaCO.) : 160.0
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Findings: (Con.)
Alice Lake
(Jim Wells County)
Two experimental and one l-inch straight mesh gill nets were set over-
night in Alice Lake during the May survey, while one experimental and one
14-inch straight mesh nets were used in the October survey. As in the 1969
netting results, game fish species once again exceeded rough fish species in
numbers (182 to 145) and total weight (92.7 pounds to 69.9 pounds) (Table 10).
The number and mean weight of gizzard shad each exhibited an increase over
the previous year's figures, as this species continues to be the most abundant
rough fish in the lake. Black bullheads hawe remained relatively abundant,
but are not considered troublesome at this time. Channel catfish, black
crappie, and white crappie have maintained good numbers, although the mean
weights of the former two declined slightly. Largemouth bass and sunfish
remained about the same as in 1969. Excluding sunfish species, no O-1 age
group game fishes were captured in gill nets.
Seining efforts failed to capture a single young-of-the-year channel cat-
fish and produced only moderate numbers of largemouth bass, white crappie,
and black crappie. Deficits in juvenile sunfishes and other forage species,
combined with those of game species, indicates heavy mortality due to pre-
dation during an extended lake draw-down. Drought conditions and domestic
consumption by the city of Alice contributed to the prolonged reduction in
water volume.
Water conditions were much the same as previously recorded. Table 11 re-
lates the close similarity between the May and October analyses results.
Recommendations:
Although sampling data indicate deficits of young game fishes in both the
Frio and Nueces Rivers, no additional stocking is recommended at this time.
Mortality rates of fingerlings stocked at these locations in past years is
believed to have been very high and frequent flooding has resulted in re-
location of these young individuals to areas far removed from the release
sites.
As stated in the 1969 progress report, flathead catfish numbers in Lake
Corpus Christi appear to be on the decline and should be bolstered by releases
of hatchery-reared advanced fingerlings. Rearing of this species has not been
undertaken on a large scale in Region V hatcheries in the past, but plans for
installation of incubating apparatus during 1971 will hopefully aid in satis-
fying the need for these fish.
Alice Lake exhibited a need for supplemental channel catfish releases,
due to heavy predation during a lake draw-down. Plans are in progress for
stocking advanced young (up to 3/4 pounds) in selected waters in the upcoming
A
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[Ve
Table 10
Alice Lake Netting Results,
May and October, 1970
| Per Cent Per Cent | Mean —
Species 7 No. | Wt. Wt. | st
Gizzard shad 33.33 543 0.5
Golden shiner 0.61 0.4 0.2
Channel catfish* 16.82 53%5 1.0
Black bullhead 10.40 14.2; : 0.4
Largemouth bass* 2.14 8.5 5.23 1.2
Warmouth* La22 0.6; 0.37 0.2
Redear sunfish* 6.73 4.0% 2.46 0.2
Bluegill* 4.90 3.1 1.91 0.2
White crappie* 13.45 3.6 8.36 0.3
Black crappie* 10.40 9.4 5.78 0.3
Total 100.00
Game fish 182 53.66
Rough fish 145 44.34
*denotes game fish
Table il
Alice Lake Water Analyses, 1970
Date: May 12 October 26
Location: At dam At dam
Depth: Surface Surface
Water temperature: 78°F
Dissolved oxygen (ppm): 8.0
Carbon dioxide (ppm): 4.0
M. O. alkalinity (ppm): 190.0
Turbidity (secchi) : 284 mm
pH: _ 8.3
Chlorides (ppm Cl ): 61.0
Total hardness (ppm CaC03): 195.0
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=12+ :
Recommendations: (Con.)
year and to evaluate the worth of such an endeavor. Alice Lake would lend
itself well to such an undertaking which could result in a betterment of the
fishery with lower mortality rates, and perhaps a reduction in overall rearing
costs to the State. Therefore, svodking of fingerling channel catfish is not
recommended is ti while keeping in mind plans to stock larger indi-
i, a cece A Releases of young flathea is also recom-~
me: en these fish become available from Region V hatcheries. This species
provides an excellent sport fish and an equally good predator, which would
assist in the control of the increasing numbers of bullheads found in Alice
Lake. we
Prepared by Roger L. McCabe Approved by
Project Leader
Date November 11, 1971 _ Elgin M. C. Dietz
Assistant for Inland Fisheries