TPWD 1965 F-6-R-12 #995: Fisheries Investigations and Surveys of the Waters of Region 5-B: Job No. B-20 Fisheries Reconnaissance
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JOB COMPLETION REPORT
As required by
FEDERAL AID IN FISHERIES RESTORATION ACT
Federal Aid Project No. F-6-R-12
FISHERIES INVESTIGATIONS AND SURVEYS OF THE WATERS OF REGION 5-B
Job No. B-20 Fisheries Reconnaissance
Project Leader: Charles T. Menn
J. Weldon Watson
Executive Director
Parks and Wildlife Department
Austin, Texas
Marion Toole Eugene A. Walker
D-J Coordinator Assistant Director for Wildlife
January 18, 1965
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ABSTRACT
Seven lakes and a part of the San Antonio River were visited during this
segment to see if any appreciable changes in the fish populations had occurred
since the previous survey.
Blue catfish (Ictalurus furcatus), the only game fish species, comprised
17.24 per cent of the total number and 6.97 per cent of the total weight of
the fish taken in the nets in Harlingen City Lake. There appeared to be a re-
lative decrease in the game fish, both in numbers and in weight.
In Bentsen State Park Lake, rough fish species including spotted gar
(Lepisosteus productus), smallmouth buffalo (Ictiobus bubalus), bluegill
(Lepomis macrochirus) and Rio Grande perch (Cichlasoma cyanoguttatum) were
dominant both in numbers and in weight with 86.36 per cent and 94.31 per cent,
respectively.
Rough fish, primarily bluegill and gizzard shad (Dorosoma cepedianum)
are dominant in Fort Brown Lake Despite their predominance, the bass and
catfish are in good condition.
Rough fish species including alligator gar (Lepisosteus spatula), spotted
gar, longnose gar (Lepisosteus osseus), threadfin shad (Dorosoma petenense),
gizzard shad, carp (Cyprinus carpio), freshwater drum (Aplodinotus grunniens)
and Rio Grande perch comprised 94.85 per cent of the total number and 95.55 per
cent of the total weight of fish taken in Llano Grande Lake.
Game fish species showed a relative increase both in numbers and in weight
in Campacuas Lake. The game fishes include channel catfish (Ictalurus punctatus),
blue catfish, warmouth (Chaenobryttus gulosus), white crappie (Pomoxis annularis)
and black crappie (P. nigromaculatus).
In Delta Orchards Lake, near Monte Alto in Hidalgo County, game fish species
including channel and blue catfish and freshwater drum showed a relative de-
crease both in number and in weight.
Rough fish species including spotted and longnose gars, gizzard shad, grey
redhorse (Moxostoma congestum), yellow bullheads (Ictalurus natalis) and Rio
Grande perch were dominant both in numbers and in weight in the San Antonio
River.
The blue catfish population showed a relative increase in numbers in Lake
Corpus Christi. Otherwise, there were no significant changes in the fish pop-
ulation.
Water hyacinth control work on Lake Corpus Christi should be continued.
However, no other developmental or management work is recommended.
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JOB COMPLETION REPORT
State of Texas
Project No. _F-6-R-12 Name: Fisheries Investigations and Surveys
of the Waters of Region 5-B
Job No. B-20 Title: Fisheries Reconnaissance
Period Covered: January 1, 1964 through December 31, 1964 __
Objectives:
To obtain current information concerning gross changes in fishing con-
ditions, and to obtain current information regarding factors influencing fish
populations.
Techniques Used:
Standard, 125-foot long, gill nets and common sense minnow seines were used
to sample fish populations. The gill nets consisted of nylon webbing, 8 feet
deep, with five 25-foot long sections of 1-, 1%-, 2-, 2%- and 3-inch square mesh.
Nets were set overnight at previously established netting stations and fish
specimens were taken from them the following morning. The netted specimens were
weighed in grams and measured in millimeters in the field, Sex and sexual de-
velopment and the occurrence of parasites in the individual specimens were re-
corded. Seined specimens were preserved and taken to project headquarters at
Mathis for identification. A list of the common and scientific names of fish
species taken during this study is included as Table l.
Routine water quality analyses were made on the various lakes and a limited
check was made of the surrounding area of each lake to determine land usage and
possible sources of pollution.
The water level data for Lake Corpus Christi were obtained from officials
at Wesley Seale Dam.
Fisherman usage of the various lakes was determined by talking to camp
owners, game wardens and sometimes to fishermen. Public access is available
to all the lakes and rivers studied in this segment.
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Table 1. Checklist of species referred to in text and tables.
Common name
Alligator gar
Spotted gar
Longnose gar
Threadfin shad
Gizzard shad
Mexican tetra
Smallmouth buffalo
Grey redhorse
Carp
Pugnose minnow
Tamaulipas shiner
Red shiner
Bullhead minnow
Flathead minnow
Channel catfish
Blue catfish
Black bullhead
Yellow bullhead
Flathead catfish
Tadpole madtom
Blackstripe topminnow
Sheepshead minnow
Mosquitofish
Sailfin molly
Amazon molly
Striped mullet
Tidewater silverside
White bass
Largemouth bass
Warmouth
Redear sunfish
Bluegill
White crappie
Black crappie
Freshwater drum
Rio Grande perch
Naked goby
Scientific name
Lepisosteus spatula Lacépede
L. oculatus (Winchell)
L. osseus (Linnaeus)
Dorosoma petenense (Giinther)
D. cepedianum (LeSueur)
Astyanax mexicanus (Filippi)
Ictiobus bubalus (Rafinesque)
Moxostoma congestum (Baird and Girard)
Cyprinus carpio Linnaeus
Opsopoeodus emiliae Hay
Notropis braytoni Jordan and Evermann
N. lutrensis (Baird and Girard)
Pimephales vigilax (Baird and Girard)
P. promelas Rafinesque
Ictalurus punctatus (Rafinesque)
I. furcatus (LeSueur)
I. melas (Rafinesque)
I. natalis (LeSueur)
Pylodictus olivaris (Rafinesque)
Schilbeodes gryinus (Mitchill)
Fundulus notatus (Rafinesque)
Cyprinodon variegatus Lacépéde
Gambusia affinis (Baird and Girard)
Mollienisia latipinna LeSueur
M. formosa (Girard)
Mugil cephalus Linnaeus
Menidia beryllina (Cope)
Roccus chrysops (Rafinesque)
Micropterus salmoides (Lacépéde)
Chaenobryttus gulosus (Cuvier)
Lepomis microlophus (Gunther)
L. macrochirus Rafinesque
Pomoxis annularis Rafinesque
P. nigromaculatus (LeSueur)
Aplodinotus grunniens Rafinesque
Cichlasoma cyanoguttatum (Baird and Girard)
Gobiosoma bosci Lacépéde
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Findings:
Harlingen City Lake
This 20-acre lake is located in downtown Harlingen and is the city's water
supply reservoir. Water in the lake originates from the Rio Grande River and
reaches the lake through a system of gravity flow irrigation canals.
Public angling is permitted on this lake without restrictions or limita-
tions, but little fishing is done due to the sizable rough fish population.
Netting - Three netting collections were made on this lake in February.
All told, 29 fish of five species were taken (Table 2). The game fish species
included blue catfish (Ictalurus furcatus) only. Channel catfish (Ictalurus
punctatus), white bass (Roccus chrysops), largemouth bass (Micropterus salmoides)
and white crappie (Pomoxis annularis) and black crappie (P. nigromaculatus)
were all taken in previous surveys but none were found in this survey.
Table 2. Results of gill netting, Harlingen City Lake, February, 1964
Species Numbers Per Cent of Per Cent of
Taken Number ) ) | Total Weight
Longnose gar ‘ a 32 a
Gizzard shad 34. 3 5.
Smallmouth buffalo ‘ ; 49.
Blue catfish*
Freshwater drum
Per Cent Game Fish
Per Cent Rough Fish
* Indicates game fish
On the basis of the limited netting data, game fish showed a relative de-
crease both in numbers and in weight. In 1963, game fish species comprised
22.54 per cent of the total number and 3.64 per cent of the total weight as
compared to 17.24 per cent of the number and 6.97 per cent of the weight in
1964.
Gizzard shad (Dorosoma cepedianum), freshwater drum (Aplodinotus grunniens),
longnose gar (Lepisosteus osseus) and smallmouth buffalo (Ictiobus bubalus), in
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that order, were the most abundant rough fish species taken. Collectively,
they comprised 77.46 per cent of the total number and 96.36 per cent of the
total weight of the fish netted.
The length-weight statistics of the fish taken in nets are shown in
Table 3. The average "K" factors are in line with those of the 1963 recon-
naissance survey.
Table 3. Length-weight statistics of fish taken with gill nets,
Harlingen City Lake, February, 1964
Standard length
(mm.
Range __Average.
Longnose gar 435-860 281-2778
Gizzard shad 163-198 84-168
Smallmouth buffalo | 403-531
Blue catfish 258-292 239-421
Freshwater drum 185-240 145-365
Seining - Seining collections were made at two stations. All told, 152
fish of 7 species were taken in the seining collections (Table 4). Mosquito-
fish (Gambusia affinis), red shiners (Notropis lutrensis) and tidewater silver-
sides (Menidia beryllina), in that order, comprised 95.40 per cent of the total
number. The most noticeable change concerned the threadfin shad (Dorosoma
petenense); they comprised less than 1 per cent by number as compared with more
than 40 per cent in 1963. This apparent "reduction" is probably due to a
seining error.
Table 4. Seining results, Harlingen City Lake, February, 1964
Per Cent of
Total Number
Threadfin shad
Red shiner
Flathead minnow
Mosquitofish
Amazon molly
Tidewater silverside
Naked goby
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Lake Conditions - Submerged vegetation is lacking due to the turbidity.
Shoreline vegetation, however, consists mainly of bulrushes mixed with a few
cattails.
Secchi disc readings of light penetration ranged from 11 to 13 inches.
It is believed that the turbidity is caused by bottom-feeding fishes which
keep silt in suspension rather than the prevailing southeasterly wind.
Recommendations - Fishermen should be encouraged to fish for catfish and
crappie. A commercial fisherman might be necessary and desirable to harvest
the rough fish in the near future.
Bentsen State Park Lake
Netting - Three gill netting collections were made on this lake in May,
1964. The second check, scheduled for November, was not made due to the
extremely low water conditions. There were only a few areas where the water
was as much as two feet deep. A total of 22 fish of five species was taken in
the netting collections. Rough fish species, including spotted gar (Lepisosteus
oculatus), smallmouth buffalo, bluegill (Lepomis macrochirus) and Rio Grande
perch (Cichlasoma cyanoguttatum) were dominant both in number and in weight
(Table 5). The only game fish species taken in the nets, warmouth
(Chaenobryttus gulosus), comprised less than 15 per cent of the total number
and 5.69 per cent of the total weight.
Table 5. Results of gill netting, Bentsen State Park Lake, May, 1964
Numbers Per Cent of Weight Per Cent of
Species Taken Total Number ‘pounds Total
Spotted gar
Smallmouth buffalo
Warmouth*
Bluegill
Rio Grande perch
Per Cent Game Fish
Per Cent Rough Fish
ole
mas
Indicates game fish
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Seining - The seining results are shown in Table 6. Mosquitofish
and threadfin shad comprised 93.02 per cent of the total number of fish taken.
Though there is a good supply of forage fish, it appears that there are few
bass and crappie in the lake to crop them.
Table 6. Results of seining, Bentsen State Park Lake, May, 1964
Numbers Per Cent of
Taken Total Number
i)
MOoonaoancodaeo
Threadfin shad
Gizzard shad
Red. shiner
Sheepshead minnow
~
Mosquitofish
Tidewater silverside
Bluegill
Rio Grande perch
The length-weight statistics are shown in Table 7. No appreciable changes
were noted for any species.
Table 7. ‘Length-weight statistics for fish taken with gill nets, Bentsen
State Park Lake, May, 1964
Standard Length
mm. Weight (grams "K" Factors
Species
Spotted gar 479-494 | 0.65-0.82
Smallmouth buffalo | 490-490 4.81-4.81
Warmouth 147-165 142-224 4.46-4.98
Bluegill 94-112 32-59 3.56-4.57
Rio Grande perch 69-144 14-113 3.73-5.20
Lake Conditions - The water level has been extremely low all year. The
upper portion of this oxbow lake is dry, but a total of approximately 10 acres
of water still remainsin the lake. By November, the lake had gone down even
lower than it was in May. For that reason the lake was not checked as
originally planned.
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Recommendations - Since the water level is so erratic, no management or
developmental work is proposed or planned. Should a more favorable water
supply become available, some management work should be initiated.
Fort Brown Lake
This 33-acre lake, located in downtown Brownsville, was drained in the
spring of 1962, dredged in the summer of that same year and refilled in the
fall. The water used in refilling the lake came from the Rio Grande River
and contained many undesirable fishes. Therefore, the lake was treated with
rotenone to remove all fishes. The state fish hatchery near Brownsville
stocked a large number of largemouth bass fingerlings in December, 1962.
Netting - Four gill netting collections were made in February, 1964, and
took a total of 162 fish of 7 species (Table 8). Of the seven species, three
were classed as game fish (channel catfish, white bass and largemouth bass).
All told, the game fish species comprised 16.66 per cent of the total number
and 37.64 per cent of the total weight.
Table 8. Results of gill netting, Fort Brown Lake, February, 1964.
Numbers Per Cent of Per Cent of
Species Taken Total Number Total Weight
Threadfin shad
Gizzard shad
Channel catfish*
White bass*
Largemouth bass*
Bluegill
Rio Grande perch
Totals
Per Cent Game Fish
Per Cent Rough Fish
* Indicates game fish
The most noticeable change in the fish population since the 1963 check is
the presence of rough fish. None were found in the 1963 check, but this year
they comprised 83.34 per cent of the total number and 62.36 per cent of the
total weight. Doubtless, these fish entered the lake from the Rio Grande which
is its main source of water.
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The length-weight statistics are presented in Table 9. All values are
considered normal for fishes in this area of Texas.
Table 9. Length-weight statistics of fish taken with gill nets, Fort
Brown Lake, February, 1964
Standard Length |
mm Weight (grams
Species
'’" Factors
Threadfin shad 119-145 51-78 63
Gizzard shad 187-288 237 163-652 328
Channel catfish 270-388 335 391-1247 840
White bass 205-244 222 306-567 436
Largemouth bass 155-331 241 94-1049) 473
Bluegill 92-111 100 29-67 46
Rio Grande perch 127-127 112-112
Seining - One seining collection was made and took 22 fish of four species
(Table 10). Bluegills and mosquitofish, in that order, comprised 90.90 per
cent of the collection. One specimen of largemouth bass, approximately 3 inches
in length, was taken and indicated that the bass had spawned. In addition to
the fish, 46 freshwater shrimp (Palaemonetes sp.) were taken in the collection.
Table 10. Seining results, Fort Brown Lake, February, 1964
Per Cent of
Total Number
Mosquitofish
Largemouth bass
Bluegill
Rio Grande perch
Lake Conditions - Secchi disc readings ranged from 19 to 28 inches, as com-
pared with 60 to 82 inches a year earlier. This noticeable change is almost
certainly due to the abundance of rough fish, most of which are bottom feeders.
The higher turbidity should aid in the prevention of excessive submerged
vegetation.
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Chemical analysis of a surface water sample revealed the following: dis-
solved oxygen 3.9 p.p.m., carbon dioxide 0.8 p.p.m., pH 8.8, and methyl orange
alkalinity 130.0 p.p.m.
Recommendations - A selective shad kill would probably be in order within
the near future. It would be beneficial to the small game fish. If the sub-
merged vegetation becomes worse, control measures will be recommended.
Llano Grande Lake
Llano Grande Lake, approximately 250 acres in size, is located 5 miles
south of Weslaco in Hidalgo County, Texas. Formerly, it was an old stream bed
of the Rio Grande River. Reconnaissance surveys were made in April and
September, 1964. Each survey consisted of six gill netting collections and
one seining collection. Generally, public access is limited to the road
crossings, but public angling is permitted without additional local restric-
tions.
Netting - Twelve gill netting collections were made on this lake. A
total of 466 fish of 14 species was taken in the netting collections (Table
11). The game fish species included channel catfish, white bass, largemouth
bass, warmouth, white and black crappie. All together, they comprised 5.15
per cent of the total number and 4.45 per cent of the total weight.
Table 11. Results of gill netting, Llano Grande Lake, April and September,
1964
Per Cent of Per Cent of
Total Number _| Total Weight
Alligator gar 1 21 4 60
Spotted gar } 15 22 34 12.24
Longnose gar 2 43 3 35
Threadfin shad 21 51 3 35
Gizzard shad 75 16.09 43 15.33
Carp 39 .37 127. 45.39
Channel catfish* 6 10
| White bass* 21
1
Largemouth bass* 4
Warmouth bass* 7
White crappie* 1
Black crappie* 5
Freshwater drum Ll
8
Rio Grande perch 28
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Per Cent Game Fish
Per Cent Rough Fish
* Indicates game fish
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Of the total fish netted, game fish showed a relative increase both in
numbers and in weight. In 1963, they comprised 3.70 per cent of the number
and 4.20 per cent of the weight as compared with 5.15 per cent of the number
and 4.45 per cent of the weight in 1964.
Rio Grande perch, gizzard shad, and carp (Cyprinus carpio) are the most
abundant rough fish present. All together, they comprised 86.27 per cent of
the total number and 78.16 per cent of the total weight. These findings are
in line with those of the 1963 survey.
The length-weight statistics are presented in Table 12. Spotted gar,
threadfin shad, gizzard shad, and warmouth showed slight decreases in ''K"
factors, while carp, channel catfish and Rio Grande perch showed increases in
"K" factors.
Table 12. Length-weight statistics of fish taken with gill nets, Llano
Grande Lake, April and September, 1964
eel sht (grams "Kt Flee eee
Species
Range — Range | Range _ Average | e Range | Range Average |
Alligator gar - 2055-2055
Spotted gar - 822-1389
Longnose gar - 465-1276
Threadfin shad - 38-318
Gizzard shad - 144-936
Carp - 57-3600
Channel catfish - 61-2268
White bass - 442-442
Largemouth bass - 217-334
Warmouth - 59-221
White crappie - 159-159
Black crappie - 57-138
Freshwater drum - 1106-1106
Rio Grande perch - 29-198
WWWWWNWENFFr OOO
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Seining - The seining results are shown in Table 13. The two collections,
one was made in April and the other in September, 1964, took a total of 971
specimens of 8 species. Mosquitofish and threadfin shad comprised 91.24 per
cent of the total number taken. Both Mexican tetra (Astyanax mexicanus) and
red shiners were abundant in the 1960 collections, but were lacking again
in this survey.
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Table 13. Seining results, Llano Grande Lake, April and September, 1964
Number Per Cent of
Species Taken Total Number
Threadfin shad 140 14.42
Mexican tetra L 0.10
Red shiner 1 0.10
Sheepshead minnow 30 3.09
Mosquitofish 746 76.82
Sailfin molly L 0.10
Tidewater silverside 41 4.23
Rio Grande perch 11 1.14
Total 971 100.00
Lake Conditions - Twelve Secchi disc readings were recorded on Llano
Grande; they ranged from 4 to 11 inches, with a mean average of 8 inches.
This comparatively shallow lake coupled with the thick silt bottom and numerous
rough fish keep the turbidity high.
Bulrushes and cattails are numerous around the shoreline of the lake.
But, these plants are not considered a problem. A few water hyacinths have
been observed in the past, but none were seen during this survey.
Dissolved oxygen ranged from 5.1 to 6.4 p.p.m., carbon dioxide ranged
from 1.2 to 2.0 p.p.m., methyl orange alkalinity from 175.0 to 190.0 p.p.m.
and pH from 8.0 to 8.2.
Recommendations - In view of the high turbidity and nature of the stream,
no developmental work is proposed or recommended. A commercial fisherman
should be allowed to harvest unlimited numbers of rough fish so long as state
and local regulations are complied with.
Campacuas Lake
Campacuas Lake is located in the same floodway as Llano Grande and covers
an area of approximately 120 acres. The lake is located between Weslaco and
Mercedes in Hidalgo County, Texas.
Netting - Eight gill netting collections were made on this lake in April
and September. A total of 149 fish of 14 species weighing 189.1 pounds was
taken in the netting collections (Table 14). The game fish species included
channel and blue catfish, warmouth, white and black crappie.
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Table 14. Results of gill netting, Campacuas Lake, April and September,
1964
ster |
Species Taken
Per Cent of
Total Weight
Per Cent of
Total Number
Alligator gar 4 14.1
Spotted gar 40 84.0 44,
Threadfin shad 6 0.5
Gizzard shad 38 11.0
Smallmouth buffalo 3 9.2
Carp 9 13.0
Channel catfish* 9 17.5
Blue catfish* 1 4.6
Striped mullet 2 3.8
Warmouth* 13 2.3
White crappie* 4 Le
Black crappie* 1 0.2
| Freshwater drum 14 27.4
Rio Grande perch 5 0.3
Per Cent Game Fish
Per Cent Rough Fish
* Indicates game fish
Since the 1963 survey, game fish species showed relative increases both in
number and in weight. In 1963, they comprised 3.75 per cent of the total
number and 1.11 per cent of the total weight as compared to 18.78 per cent of
the number and 13.64 per cent of the weight in 1964. This "change" in large
part is due to the fact that more data are available from the 1964 survey and
that the state fish hatchery stocked a sizable number of crappie in the lake.
The length-weight statistics are presented in Table 15. Since the 1963
check, there appears to be a relative increase in the average "K" factors of
the gizzard shad and smallmouth buffalo. But there appears to be a relative
decrease in the average "K'"' factors of the channel catfish, warmouth and
freshwater drum. Otherwise, the average "K" factors appear to be the same.
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Table 16.
total numbers taken.
collections.
Table 15.
-13~-
Lake, April and September, 1964
aes SCS CCO!™!™*~=<‘“‘ _S™SOSOC;.CCC.....OCOtw#é‘C(SSS!!!CS
| Standard Length
(mm. )
Alligator gar
Spotted gar
Threadfin shad
Gizzard shad
Smallmouth buffalo
Carp
Channel catfish
Blue catfish
Striped mullet
Warmouth
White crappie
Black crappie
Freshwater drum
Rio Grande perch
Seining -
Table 16.
| 318-893
| 336-610
126-135
122-276
280-382
157-352
193-418
438-438
307-335
106-162
152-162
144-144
181-360
94-100
548
508
130
206
322
261
329
438
321
122
156
144
291
98
Length-weight statistics of fish taken with gill nets, Campacuas
Numbers
Taken
Weight (grams) "K" Factors
Range Average
251-7598 2718 0.78-1.06 0.90
115-2041 1068 0.61-0.92 0.77
39-49 43 1.74-2.33 1.96
31-417 190 1.52-2.02 1.78
879-2296 1389 3.53-4.11 3.88
120-1361 658 2.82-3.68 3.08
111-2041 882 |; 1.49-2.16 1.85
2098-2098 2098 2.49-2.49 2.49
737-992 865 2.54-2.63 | 2.59
22-184 79 3.19-4.55 3.91
| 115-158 134 | 3.27-3.71 3.51
| 103-103 103 3.44-3.44 3.44
159-1505 887 2.58-2.58 2.58
36-43 40 4.10-4.43 4.28
Two seining collections were made; the results are shown in
Sailfin molly (Mollienesia latipinna), threadfin shad, and pugnose
minnow (Opsopoeodus emiliae), in that order, comprised 86.89 per cent of the
All told, 648 fish of 12 species were taken in the two
Seining results, Campacuas Lake, April and September, 1964
Per Cent of
Total Number
Threadfin shad
Mexican tetra
Tamalipas shiner
Red shiner
Mosquitofish
Tidewater silverside
Bullhead minnow
Pugnose minnow
Sheepshead minnow
Sailfin molly
Rio Grande perch
Naked goby
185
117
261
10
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ron
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Lake Conditions - Eight Secchi disc readings were taken; they ranged from
5 to 10 inches with a mean average of 7 inches. Strong, southeasterly winds,
coupled with the thick silt bottom and numerous rough fish, keep the turbidity
high. As a result, submerged vegetation is not a problem. Shoreline vegetation
consists of bulrushes and cattails.
Recommendations - A commercial fisherman should be allowed to crop the
rough fish. No developmental work is proposed or recommended.
Delta Orchards Lake
Delta Orchards Lake, a 2,200 acre surface irrigation reservoir near Monte
Alto, is a part of the Hidalgo and Willacy County Water Control and Improvement
District No. 1. The reservoir contains approximately 20,000 acre-feet of water
which is used to irrigate nearly 70,000 acres of farm land. Most of the water
comes from the Rio Grande River via a system of gravity flow irrigation canals.
Public angling is permitted for a 25-cent fee per person per day. But
trotline fishing is prohibited except to certain persons who are issued special
permission.
Netting - In May and November, 1964, 10 netting collections took a total
of 128 fish of 9 species (Table 17). The game fish species taken in the nets
included channel and blue catfish, and freshwater drum. Normally, the drum
is considered a rough fish species here in south Texas, but it is classed as
a game fish in this case because anglers at Delta Orchards Lake harvest them
in large numbers the year around.
Table 17. Results of gill netting, Delta Orchards Lake, May and November,
1964
Per Cent of i Per Cent of
Total Number Total Weight
Spotted gar
Longnose gar
Gizzard shad
Smallmouth buffalo
Carp
Channel catfish*
Blue catfish*
Striped mullet
Freshwater drum*
8
6
4
4
al,
6
«9
a9
wll
Per Cent Game Fish
Per Cent Rough Fish
* Indicates game fish
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<15-
Of the total fish taken in the nets, game fish species comprised 23.43
per cent of the number and 17.18 per cent of the weight. A year before, they
comprised 52.91 per cent and 34.24 per cent by number and weight, respectively.
Therefore, it appears that there is a definite decrease both in numbers and in
weight. Most of this decrease may be attributed to the disappearance of the
crappie. For this reason a sizable number of crappie have been stocked by the
state fish hatchery at Brownsville. The freshwater drum has also declined,
both in numbers and in weight. In 1963, they comprised 17.44 per cent of the
number and 8.36 per cent of the weight as compared to 1.56 per cent of the
number and 0.50 per cent of the weight in 1964. This "decline" is not under-
stood.
The average "K'' factors, or indices of physical condition, of all fish
remained about the same. The length-weight statistics are presented in Table
18.
Table 18. Length-weight statistics of fish taken from Delta Orchards
Lake, May and November, 1964
Standard Length
(mm. ) Weight (grams) "K' Factors
Species Range Average Range Average | Range Average
Spotted gar 337-600 | 317-1332 00
Longnose gar 429-885 306-3742
Gizzard shad 125-220 41-219
Smallmouth buffalo 228-437 431-3232
Carp 116-363 49-1446
Channel catfish 827-392 | 567-1021
Blue catfish 164-415 72-1361
Striped mullet 438-479 2155-2778
Freshwater drum 190-209 238-265
Seining - Two seining collections took a total of 914 fish of 13 species
(Table 19). Tidewater silversides, mosquitofish, sheepshead minnows (Cyprinodon
variegatus) and red shiners, in that order, comprised 91.79 per cent of the
total number. The most apparent increase concerned the red shiner. They com-
prised 0.27 per cent of the 1963 collections as compared to 13.02 per cent of
the 1964 collections. The threadfin shad showed a relative decrease from
13.74 per cent in 1963 to 0.44 per cent in 1964, and the Tamaulipas shiner
(Notropis braytoni) comprised 18.60 per cent of the 1963 collections as com-
pared to 2.63 per cent in 1964. No other significant changes were noted.
--- Page 18 ---
=i6-
Table 19. Seining results, Delta Orchards Lake, May and November, 1964
Per Cent of
Total Number
Threadfin shad 4 0.44
Gizzard shad 9 0.98
Mexican tetra 6 0.66
Tamaulipas shiner 24 2.63
Red shiner 119 13.02 |
Bullhead minnow 4 0.44
Gulf killifish 4 0.44
Sheepshead minnow 162 17.72
Mosquitofish 251 27.46
Sailfin molly 11 1.20
Tidewater silverside 307 33.59
Rio Grande perch 6 0.66
Naked goby 7 0.76
Lake Conditions - Other than thick growths of algae, aquatic vegetation is
lacking in the lake. This may be attributed to the fact that the prevailing
strong, southeasterly winds keep the silt in suspension in this shallow lake.
Dissolved oxygen values ranged from 2.8 to 3.4 p-p-m., carbon dioxide
values ranged from 0.20 to 1.0 p.p.m., methyl orange alkalinity ranged from
130 to 165 p.p.m., and pH ranged from 8.2 to 8.4. All values are considered
normal for this area.
Recommendations - Since wild fish from the Rio Grande River have access to
Delta Orchards Lake, population control work would be ineffective and, there-
fore, is not recommended. It is recommended that a commercial fisherman be
permitted to harvest as many rough fish as possible.
Additional crappie should be stocked if they are needed.
San Antonio River
Netting - Five gill netting collections were made on the San Antonio River
and Cibolo Creek in June, 1964. A total of 77 fish of 9 species weighing 73
pounds was taken (Table 20). Rough fish species, including spotted and longnose
gars, gizzard shad, grey redhorse (Moxostoma congestum), yellow bullheads
(Ictalurus natalis) and Rio Grande perch were predominant both in number and
weight. Of the three game fish species taken, channel and flathead catfish
(Pylodictus olivaris) are the most important sport fishes; however, their
--- Page 19 ---
“1F-
numbers are limited. Again, no carp were taken. There was no significant
change in the fish population since the basic survey of 1962 (see completion
report for Job B-18, Project F-6-R-10).
Table 20. Results of gill netting, San Antonio River, June, 1964
| ber
Species Taken
Per Cent of
Total Weight
Per Cent of
Total Number
Spotted gar 7 9.09 11.2 15.34
Longnose gar 7 9.09 9.3 12.74
Gizzard shad 5 6.49 1.5 2.06
Grey redhorse 11 14.29 8.3 11.37
Channel catfish* 12 15.59 11.9 16.30
Yellow bullhead 1 1.30 Oud 0.27
Flathead catfish* 6 7.79 22.9 31.37
Bluegill* 4 5.19 0.4 0.55
Rio Grande perch 24 31.17 703 10.00
Per Cent Game Fish
Per Cent Rough Fish
* Indicates game fish
The length-weight statistics are presented in Table 21. The average "K"
factors are in line with those of the 1962 basic survey.
Table 21. lLength-weight statistics of fish taken with gill nets, San
Antonio River,. June, 1964
Standard Length
(mm. ) Weight (grams) "K" Factors
Species Range Average Range Average
Spotted gar 379-560 459 327-1276 727 0.60-0.86 0.71
Longnose gar 412-675 530 288-1191 602 0. 0.36
Gizzard shad 142-235 196 50-281 172 1. 2.07
Grey redhorse 175-310 237 131-624 341 1. 2.35
Channel catfish 190-439 273 109-1729 448 Ls 1.89
Yellow bullhead | 158-158 158 | 89-89 89 Zs 2625
Flathead catfish | 316-495 443 | 510-2282 1729 1. 1.86
Bluegill 93-98 95 | 35-43 40 4. 4.68
Rio Grande perch | 111-192 73-466 5. 5.94
--- Page 20 ---
-18-
Seining - Ten seining collections were made during this survey. The
results are presented in Table 22. Mosquitofish, red shiners and pugnose
minnows, in that order, comprised 92.59 per cent of the seining collection.
The red shiners, however, decreased from 62.14 per cent in 1963 to 22.68 per
cent in 1964 while the mosquitofish showed an increase from 29.83 per cent
in 1963 to 60.42 per cent in 1964.
Table 22. Seining results, San Antonio River, June, 1964
Per Cent of
Total Number
Numbers
Taken
Species
Smallmouth buffalo
Pugnose minnow
Red shiner
Flathead minnow
Channel catfish
Black bullhead
Tadpole madtom
Blackstripe topminnow
Mosquitofish
Sailfin molly
Amazon molly
Largemouth bass
Bluegill
White crappie
Rio Grande perch
COONDODODOOCOONON SD
Recommendations - Every reasonable effort should be made to prevent
industrial, municipal and soil pollution in the river. This, of course,
will require the combined efforts of many people and agencies.
The sportsmen will be limited to catfish angling in the river, Cibolo
Creek has a moderate population of largemouth bass in addition to a good cat-
fish population. Since the catfish is one of the principal game fish species
in the river, commercial fishermen should not be allowed to take them and every
effort should be made to protect and propagate them.
No developmental work is presently proposed or recommended.
Lake Corpus Christi
Netting - A total of 40 gill netting collections was made on Lake Corpus
Christi during January, April, July and October, 1964. All told, these nets
took 1,712 fish of 17 species (Table 23).
--- Page 21 ---
«19%
Table 23. Results of gill netting, Lake Corpus Christi, 1964
i
Number Per Cent of Weights Per Cent of
Species Taken Total Number ounds Total Weight
Alligator gar 8 0.47 199.8 11.71
Spotted gar 137 8.00 286.2 16.77
Longnose gar 102 5.96 423.0 24.79
Gizzard shad 549 32.07 181.8 10.65
Smallmouth buffalo BL 1.81 76.0 4.45
Carp 8 0.47 19.0 1.11
Channel catfish* 112 6.54 34.9 2.04
Blue catfish* 360 21.03 234.7 13.75
Flathead catfish* 1 0.06 349 0.23
White bass* 50 2.92 28.7 1.68
Largemouth bass* 6 0.35 6.4 0.37
Warmouth* 2 0.12 0.3 0.02
Redear sunfish* 4 0.23 0.5 0.03
Bluegill 11 0.64 1.2 0.07
White crappie* 109 6.36 58.7 3.44
Black crappie* 26 Ls 52 15.4 0.90
Freshwater drum 196 11.45 136.3 7.99
Per Cent Game Fish
Per Cent Rough Fish
* Indicates game fish
Rough fish species, including alligator gar (Lepisosteus spatula),
spotted and longnose gars, gizzard shad, smallmouth buffalo, carp, bluegill,
and freshwater drum comprised 60.87 per cent of the number of fish netted
and 77.54 per cent of the total weight. In 1963, the rough fish species com-
prised 58.81 per cent of the number of fish netted and 72.86 per cent of the
total weight. Overall, there does not appear to be any significant change in
the fish population since the 1963 reconnaissance survey. Among the individual
species, there appears to be a relative decrease in the gizzard shad populations.
They comprised 32.07 per cent of the total number taken in 1964 as compared to
36.07 per cent in 1963. Otherwise, there were no significant changes.
The principal game fish species include channel, blue and flathead catfish,
white bass, largemouth bass, warmouth, white and black crappie. Of these,
the blue catfish population showed a relative increase. In 1963, they comprised
18.32 per cent of the total number and 11.50 per cent of the total weight as
compared to 21.03 per cent of the number and 13.75 per cent of the weight in
1964. The other game fish species remained about the same as they did a year ago.
--- Page 22 ---
* iis
The white bass have not greatly increased in the last year. This, to a
large extent was due to the unfavorable spawning conditions in the river.
Crappie and catfish fishing remained good during the year but largemouth bass
fishermen had less than good fishing. This was attributed to the extremely
low water level during the spring.
The length-weight statistics are presented in Table 24. No significant
changes were noted.
Table 24. Length-weight statistics for fish from Lake Corpus Christi, 1964
Standard Length
ae (mm. ) Weight (grams) "K' Factors
Species Range Average 9 Range
Alligator gar 612-1340 985 2070-26762! 11340 |0.90-1.12 1.04
Spotted gar 289-730 486 190-2665 948 10. 0.
Longnose gar 404-983 680 218-5330 1787 | 0. 0.
Gizzard shad - 122-272 184 29-455 151 /1. 1.
Smallmouth buffalo | 127-438 283 77-3827 1112 | 3. he
Carp 265-377 324 510-1644 1077 | 2. 3.
Channel catfish 59-370 197 3-936 141 | 0. 1.
Blue catfish 135-556 250 33-2892 297 | 1. Ls
Flathead catfish 437-437 437 1758-1758 1758 | 2. 2.5
White bass 130-318 194 66-1276 264 | 2. 3.
Largemouth bass 216-329 250 263-992 483 | 2. 2.
Warmouth 106-127 117 49-74 62 | 3. Bie
Redear sunfish 104-134 123 39-112 80 | 3. he
Bluegill 97-112 101 32-57 42 |3. 3.
White crappie 78-269 191 14-624 248 | 2. 3.
Black crappie 113-234 188 45-539 273 | 2. 3.
Freshwater drum 120-346 44-1588 2. 2.
Seining - Thirty-five seining collections took a total of 20,148 fish of
19 species (Table 25). Tidewater silversides, mosquitofish, gizzard shad and
red shiners, in that order, comprised 87.74 per cent of the fish seined. In
addition to the large numbers of these fish, they were evenly distributed
throughout the reservoir.
--- Page 23 ---
1+
Table 25. Seining results, Lake Corpus Christi, 1964
Per Cent of
Total Number
Numbers
Taken
Species
Threadfin shad O.
Gizzard shad L7s
Mexican tetra QO.
Pugnose minnow 2.
Red shiner 10.
Bullhead minnow 196 0.
Flathead minnow 3 QO.
Channel catfish 4 QO.
Sheepshead minnow 596 Dew
Mosquitofish 5988 29.
Sailfin molly 266 1.
Amazon molly 516 2
Tidewater silverside 6020 29.
Largemouth bass 4 0.
Warmouth 8 QO.
Redear sunfish 13 Os
Bluegill 361 l.
White crappie 1 QO.
Rio Grande perch Ow
Stomach Analyses - Unidentifiable fish remains and shad were found in
the stomachs of both alligator and spotted gars. Mostly shad were found in
the white bass, white crappie and blue catfish stomachs. In addition to fish
remains, a Rio Grande perch was taken from a largemouth bass' stomach.
Lake Conditions - The water level reached its lowest point on August 8,
1964, when the level was recorded at 79.77 feet. In July, the gates were
closed and the heavy fall rains filled the lake to its new capacity of 94
feet on October 6, 1964 (Table 26).
Undoubtedly, the fluctuating water level affected the spawning of
centrarchids, especially largemouth bass and crappies. Since there was very
little water coming into the lake in the spring, it is doubtful that the white
bass had a good spawn.
Secchi disc readings of light penetration ranged from 7 to 27 inches.
The water was consistently clearer in the lower reaches of the lake. Water
analyses were made at two stations and all values were considered normal
for this region.
--- Page 24 ---
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--- Page 25 ---
223
Recommendations - Water hyacinth control work should, if at all possible,
be continued. The volume of Lake Corpus Christi has increased considerably
and the water hyacinths will certainly become a major problem in the near
future.
No other developmental or management work is recommended.
For information purposes a comparison of netting success is included as
Table 27.
© a i
PO poh * e
Prepared by Charles T. Menn Approved by LO fpetyrts A bb CCH
Project Leader ’ Coordinator
Date January 18, 1965 Kenneth C. Jurgens
Regional Supervisor
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