TPWD 1960 F-6-R-7 #620: Resurvey of Waters of Region 8-B: Job Completion Report, Dingell-Johnson Project F-6-R-7, Job B-11
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Report of Fisheries Investigations
Resurvey of Waters of Region 8-B
by
Charles T. Menn
Assistant Project Leader
Dingell-Johnson Project F-6-R-7, Job B-11
July 1, 1959 - December 31, 1959
H. D. Dodgen - Executive Secretary
Texas Game and Fish Commission
Austin, Texas
Marion Toole Kenneth C. Jurgens & William H. Brown
Coordinator Assistant Coordinators
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ABSTRACT
Four lakes including Casa Blanca Lake, Fort Brown
Lake, Campacuas Lake and Llano Grande Lake were re-
surveyed in an effort to discover any changes in the
fish populations.
In Casa Blanca Lake, near Laredo, Webb County,
threadfin shad (Dorosoma petenense), gizzard shad (D.
cepedianum), black bass (Micropterus salmoides), and
white crappie (Pomoxis annularis) showed relative in-
creases in numbers while river carpsucker (Carpiodes
carpio) and freshwater drum (Aplodinotus grunniens)
showed relative decreases. These changes are mostly an
improvement over past years and are probably due to the
additional water volume of the lake.
It was found that carp (Cyprinus carpio), gizzard
shad and Rio Grande cichlids (Cichlasoma cyanoguttatum)
have become established in Fort Brown Lake, by entering
through the untended pump screens. Although submerged
vegetation in this lake has not reached a critical stage,
its control is worthy of some consideration.
Netting and seining samples on Llano Grande and
Campacuas Lake revealed that rough fish remain dominant
despite the rotenone treatment in May 1959. During
the first part of this segment, 7,075 fingerling black
bass were stocked in Campacuas Lake.
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Job Completion Report
State of TEXAS
Project No. F-6-R-7 Name: Fisheries Investigations and Surveys
of the Waters of Region 8-8.
Job No. B-11 Title: Resurvey of the Waters of Region 8-B.
Period Covered: duly 1, 1959 ~ December 31, 1959
OBJECTIVES
To determine the present status of waters and fish populations which have been
previously surveyed in Project F-6-R.
PROCEDURE
Experimental gill nets were used in all cases to gather information concerning
the relative abundance and weights of fish species. Seining collections were made
only on Llano Grande and Campacuas Lake in addition to the netting collections.
Netted specimens were weighed (in grams) and measured (in millimeters) in the
field. Sex, state of sexual development, and the occurrence of parasites of the indi-
vidual specimens were also noted and recorded in the field. Seined specimens were
preserved in 10 percent formalin and taken to the regional fisheries laboratory for
identification.
FINDINGS
Casa Blanca Lake
A total of 16 experimental gill nets was set in Casa Blanca Lake during this
resurvey period. Eight collections were made in October and eight were made in
December 1959. The 16 nets took 492 fish of 11 species which weighed 213,796 grams.
On the basis of these netting results compared with those of the previous resurvey
(F-6-R-5, Job B-1l), threadfin shad (Dorosoma petenense), gizzard shad (D. cepedianum),
black bass (Micropterus salmoides), and white crappie (Pomoxis annularis) showed
relative increases in numbers, while river carpsuckers (Carpiodes carpio) and fresh-
water drum (Aplodinotus grunniens) showed relative decreases.
Table 1 shows the numbers of fish collected in the 16 nets at the eight stations
on the lake. According to this table, rough fish comprised 50.41 percent by number
and 59.74 percent by weight as compared to the netting results of 1958 when these
species comprised 70.32 percent by number and 90.96 percent by weight of the total
net catch. Threadfin shad appear to be well established in this lake, comprising
9.95 percent of the netted specimens, whereas none was netted in the previous resurvey.
No seining collections were made during this segment.
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Table 2 shows the weights (in grams) of fish collected and Table 3 shows the
lengths, weights, and "K" factors of the fish. No significant changes in the condition
of the fish, as expressed by the "K" factors, were found.
No chemical analyses of water were made during this resurvey period. However,
Secchi disk readings, taken at each netting station, were found to range from ll=- to
28-inches. This is somewhat less than the 54-inch maximum reading found in the
previous resurvey.
Fort Brown Lake
During this resurvey period, two experimental gill nets were set in Fort Brown
Lake, at Brownsville. A total of 70 fish of seven species was collected. Four species
were classified as game fish and three species were classified as rough fish.
Black bass and channel catfish (Ictalurus unctatus) were the only species stocked
in the lake following B Gsori treatment in 19: 1950. However, this resurvey revealed
that gizzard shad, carp (Cyprinus carpio), Rio Grande cichlids (Cichlasoma cyanoguttatum),
bluegill sunfish (Lepomis macrochirus), warmouth bass (C haenobryttus aes suieeue, blue
catfish (Ictalurus furcatus) and white crappie are now present in the lake. Since this
lake is dependent on the Rio Grande for its water, all incoming water has to be
"screened" to prevent the entry of fish.
At the time of the renovation, the City of Brownsville agreed to install and
maintain inlet sereens. Project personnel have seen the screens filled with debris
which stopped them up. Consequent water flow over the screens and "blow out" holes
in them have allowed rough fish from the river to become established in the lake.
Attempts were made in Job S-1, (F-6-R-7) to net carp from the lake but mostly
Rio Grande cichlids were removed. Attempts to get large flathead (Pylodictus olivaris)
and blue catfish from the stilling basin below Anzalduas Reservoir were cancelled when
the International Boundary and Water Commission decided against draining the basin.
Catfish, if stocked, should make an effective natural control on the cichlids and sunfish.
The rough fish comprised about 43 percent by number and about 70 percent by
weight of the netted specimens taken in this resurvey. Table 4 shows the numbers of
fish caught during this study at the two net stations. Also, the percentage of each
species is given in this table.
Table 5 shows the weights of the species collected by station and Table 6 shows
the average, minimum and maximum lengths, weights, and "K" factors.
On the basis of these netting collections, carp ranked first by weight and second
by number. Despite the established populations of rough fish, black bass and channel
catfish and blue catfish appear to be in good condition and anglers are able to catch
nice strings of bass and catfish.
The noxious vegetation in the lake, primarily Najas sp., Chara sp. and Ceratophylium
sp., will, in time, create a definite fisheries problem. Since this is a very shallow
ox~bow iake, annual plant control will probably be necessary to lessen the problem.
As yet, no summer kill of fish due to decaying vegetation has been observed or reported.
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Llano Grande and Campacuas Lakes
Pive seining collections and eight gill net collections were made on Llano Grande
and Campacuas Lakes during this segment. Three gill nets in Campacuas Lake took a
total of 23 fish of 5 species weighing 10,456 grams. Rough species, gizzard shad
and carp, were found to comprise 56.52 percent by number and 86.10 percent by weight
of the fish netted despite the rotenone treatment in May 1959 (Project F-1i-D-3, Job
16a-18). Gizzard shad appeared to be the most abundant species in the lake, comprising
52.17 percent by number (Table 7). Three species of game fish (channel catfish, war-
mouth bass, and white crappie) comprised 43.48 percent by number and 13.90 percent by
weight. One white crappie, taken during this resurvey, was undoubtedly missed by the
rotenone treatment in May 1959 since none was restocked in the lake.
Eight channel catfish, which were stocked in June 1959, were recaptured during
this resurvey. The catfish ranged from 7- to 8-inches in length; thus showing a
physical growth of over 6 inches in the initial six month period. All of the catfish
were lively and thus returned to the lake after length and weight measurements were
recorded, On July 8, 1959, 7,075 fingerling largemouth bass from 2 to 3 inches in
length were stocked in Campacuas Lake.
Two seining collections were made in "Green's Ditch" during this resurvey. It
was found that tetra (Astyanax fasciatus), gizzard shad, carp and Rio Grande cichlids
were present in this drainage canal although it was treated with rotenone in conjunc-
tion with Campacuas Lake.
Five netting collections in Llano Grande Lake took 88 fish of eight species. It
was found that rough species remain dominant in this lake as well as "Paradise Creek"
which flows into this lake on the west end.
According to the net collections, as shown in Table 9, rough fish (alligator gar
(Lepisosteus spatula), spotted gar (Lepisosteus productus), gizzard shad, carp and
Rio Grande cichlids) comprised 87.50 percent by number and 96.69 percent by weight
(Table 10).
Prepared by _ Charles T. Menn Approved by
Assistant Project Leader Director Inland Fisheries Division
Date June 9, 1960
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Table lL. Numbers of Fish Taken in Experimental Gill Nets
from Casa Blanca Lake, October and December 1959.
STATIONS
Species 1 2 3 iF 5 6 7 8 Total Percent
ih Se ne en ne ee Md
Dorosoma petenense 12 9 10 re) 11 4 () 3 “hg 9.95
Dorosoma cepedianum 9 16 6 9 17 15 6 16 9k 19.11
Ictiobus bubalus re) fe) 1 3 5 0 7 3 19 3.86
Carpiodes carpio 4 6 8 5 18 8 11 1 61 12.40
Cyprinus carpio 0 re) i 1 @) Af ) 0 3 0.61
Ictalurus punctatus* re) ) 5 2 1 6 3 5 22 LUT
Micropterus salmoides* 3 1 1 4 3 2 5 ) 19 3.86
Lepomis macrochirus* 4 1 (@) re) 2 1 ) 3 1l 2.2h
Pomoxis annularis* 36 50 14 17 19 el 13 22 192 39.02
Aplodinotus grunniens 6) ) 1 1 3 2 2 3 12 2.44
Cichlasoma cyanoguttatum fe) 1 0 0 1 8 ) 0 10 2.04
Total 68 8h 47 he 80 68 7 56 492 100.00
Percent by Station 13,62 i707 9.55 8.54 16.26 13.82 9.55 11.39 100,00
Rough Fish 25 32 27 19 55 38 26 26 248
Percent Rough Fish 36.76 38.09 57.45 45.2h 68.75 55.88 55.32 46.43 50.41
Game Fish* 43 52 20 23 25 30 21 30 2k
Percent Game Fish 63.24 61.91 42.55 54.76 31.25 4b.i2 44.68 53.57 49.59
* Indicates Game Fish
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Table 2. Grams of Fish Taken in Experimental Gill Nets
from Casa Blanca Lake, October and December 1959
Stations
Species 1 2 3 4 5 6 7 8 Total Percent
a YC otal = Percent
Dorosoma petenense 787 549 465 0 828 264 O 125 3,018 1.41
Dorosoma cepedianum 699 1,417 633 1,093 2,345 1,854 779 2,361 11,181 5.23
Ictiobus bubalus ©) ©) 2,070 5,811 9,483 0 12,729 5,726 35,819 16.75
Carpiodes carpio 4423 5,854 11,113. 6,039 20,710 7,795 10,408 1,247 67,589 31.61
Cyprinus carpio 0 ) 373 893 @) ©) 0) @) 1,266 0.60
Ictalurus punctatus* 0 fo) 7,144 3,260 fo) 7,995 3,303 786 22,488 10.51
Micropterus salmoides* 8,846 145 1,928 4141 3,159 230 5, 68h 0 24,133 11.29
Lepomis macrochirus* 155 0 ©) 0 77 36 0 193 461 0.22
Pomoxis annularis* 6,415 8,672 3,043 3,783 5,122 4 323 2,592 5,051 39,001 18,24
Aplodinotus grunniens @) ) 794 re) 1,400 1,035 714 1,789 5,732 2.68
Cichlasoma cyanoguttatum re) ) ) fe) 335 2,773 @) fe) 3,108 1.46
Total 21,325 16,637 27,563 25,020 43,459 26,305 36,209 17,278 213,796
Percent by Station 9.97 Ts7o 12.89 11.71 20.32 12.31 16.93 8.09 100.00
Rough Fish 5,909 7,820 15,448 13,836 35,101 13,721 24,630 11,2h8 127,713
Percent Rough Fish 27.71 47.00 56.05 55.30 80.77 52.16 68.02 65.10 59.74
Game Fish* 15,416 8,817 12,115 11,184 8,358 12,584 11,579 6,030 86,083
Percent Game Fish 72.29 53.00 43.95 4.70 19.23 47.84 31.98 34.90 40.26
* Indicate Game Fish
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Species
Dorosoma petenense
Dorosoma cepedianum
Ictiobus bubalus
Carpiodes carpio
Cyprinus carpio
Ictalurus punctatus
Micropterus salmoides
Lepomis macrochirus
Pomoxis annularis
Aplodinotus grunniens
Cichlasoma cyanoguttatum
Table 3.
Standard
Min. Max.
115 170
130 263
350 430
265 400
225 320
349 510
175-485
g2 125
120 310
195 360
162 195
Lengths, Weights, and "K" Factors of Fish Taken
from Casa Blanca Lake, October and December 1959
Length
Avg.
141.94
177.04
385.11
335-52
261.67
419.73
326.68
103.27
194.06
279.92
182.70
Weight in Grams
Min. Max. Avg.
35 95 61.59
42 -332s«119.53
1,361 2,438 1,885.21
482 1,984 1,122.77
373 978 748.00
751 2,934 1,550.46
115 3,204 1,270.16
34 83 45 £00
42 = 879~— 202.77
150 1,021 525.83
200 khs 347.80
ike
Min.
2.21
2.60
1.54
1.97
5.38
1.09
1.68
5.32
Factor
Max.
2.63
2.37
4.16
4g
2.98
2.27
3.48
435
3.19
2.63
6.48
Avg.
2.11
1.98
3.31
2.87
2.76
1695
2.55
3.97
2.45
2.15
5.62
Rank
by No.
10
[ee) Nn ww
Rank
by Wt.
Ww OV oO
10
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Table 4, Numbers of Fish Taken in Experimental Gill Nets
from Fort Brown Lake, September 1959.
Station
Species 1 2 Total Percent
-Dorosoma cepedianum 1 ) i 1.42
Cyprinus carpio 7 11 18 25.72
*Ictalurus punctatus h 3 vi 10.00
*Ictalurus furcatus 1 4 5 7.14
*Micropterus salmoides h. 2 6 8.57
*Lepomis macrochirus 16 6 22 31.43
Cichiasoma cyanoguttatum 0 Ll La 15.72
Total 33 aT 70
Percent 47.14 52.86 100.00
Rough Fish 8 22 30
% Rough Fish 2h ,oh 59.46 42.86
*Game Fish 25 15 ho
(Game Fish 75.76 4O.54 57.14
* Indicates Game Fish
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Table 5. Grams of Fish Taken in Experimental Gill Nets
from Fort Brown Lake, September 1959.
Station
Species L 2 Total Percent
Dorosoma cepedianum 462 O 462 1.24
Cyprinus carpio 7,286 16,841 2h , 127 64.95
*Ictalurus punctatus 2,274 1,779 4,053 10.92
*Ictalurus furcatus 680 3,191 3,871 10.42
*Micropterus salmoides 1,408 65 1,473 3.96
#Lepomis macrochirus 1,210 417 1,627 4. 38
Cichlasoma cyanoguttatum ) 1,531 14531 4.13
Total 13,320 23, 62h 37,144
Percent 35.86 64.14 100.00
Rough Fish 7,748 18,372 26,120
Percent Rough Fish 58.17 77.1e 70.32
#Game Fish 5,572 5,452 11,024
Percent Game Fish 41,83 22.88 29.68
* Indicates Game Fish
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Species
Dorosoma cepedianum
Cyprinus carpio
ictalurus punctatus
Ictalurus furcatus
Micropterus salmoides
Lepomis macrochirus
Cichlasoma cyanoguttatum
- Indicates only one fish.
Table 6,
9.
Lengths, Weights, and "K" Factors of Fish Taken
from Fort Brown Lake, September 1959.
Standard Length.
Min. Max. Avg.
304
290
290
116
94
140
278
410
360
431
306
150
164
278.00
305«L7
319.86
354.40
191.17
123.73
147.91
Weight in Grams
Min.
851
418
Sat
32
38
100
Max.
462
2,098
794.
1,503
794
12h
205
Avg.
462.00
1,340.39
519.00
774.20
245.50
76.23
139.18
"K" Factor
Min. Max. Avg.
- 2,15 2.15
2.08 h.ok 2.9h
1.35 2.33 1.78
1.23 4.60 1.54
2.11 2.77 2.38
3.08 5.16 3.74
3.11 5.61 4.2)
Rank
by No.
Rank
by Wt.
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Species
Dorosoma cepedianum
Cyprinus carpio
Ictalurus punctatus*
Chaenobryttus gulosus*
Pomoxis annularis*
Total
Percent by Station
Rough Fish
Percent Rough Fish
Game Fish*
Percent Game Fish
* Indicates Game Fish
Table 7.
No.
2
13.04
3
100.00 100.00
)
0.00
Wt.
574
574
5.48
57h
6)
0.00
No.
7
30.43
>
71.43
2
28.57
Stations
Wt.
1,048
6,124
109
150
7,431
71.07
7,172
96.51
259
3.49
No.
y)
13
56.53
5
38.46
8
61.54
Wt.
1,257
804
fe)
390
2,451
23.45
1,257
51.29
1,194
48.71
Numbers and Grams of Fish Taken in Experimental
Gill Nets from Campacuas Lake, November 1959.
Total
No. Wt.
12 2,879
1 6,124
8 913
1 150
1 390
23 10,456
13 9 ,003
56.52 86.10
10 1,453
43.48 13.90
Percent
No. Wt.
52.17 27.53
4.35 58.57
34.78 8.73
4.35 1.44
4.35 3-73
100.00 100.00
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Table 8.
Species
Dorosoma cepedianum
Cyprinus carpio
Ictalurus punctatus
Chaenobryttus gulosus
Pomoxis annularis
- Indicates only one fish.
Lengths, Weights and "K" Factors of Fish Taken
from Campacuas Lake, November 1959.
Standard Length
Min. Max.
135 270
- 2ho
175 210
- 150
- 2ho
Avg.
208 . 33
240.00
192.50
150.00
240.00
ll.
Weight in Grams
Min. Max.
45 390
- 315
93 140
- 150
«“ g70
Avg.
239.92
315.00
114,13
150.00
390.00
mK
Min.
1.83
1.47
Factor
Max. Avg.
2.28 2.07
2.28 2.28
1.83 1.60
Webh W bh
2.82 2.82
Rank
by No.
Rank
by Wt.
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Table 9. Numbers of Fish Taken in Experimental Gill Nets
from Llano Grande Lake, November 1959.
Stations
3 a Percent
Lepisosteus spatula 3 @) 5 3 O il 12.50
Lepisosteus productus 8 i 1 1 2 13 14.77
Dorosoma cepedianum h 2. ake) Ly 13 45 51.13
Cyprinus carpio ) 4 1 1 1 T 7.96
*Ictalurus punctatus e) ¢) 3 1 re) 4 4k
*Micropterus salmoides fe) ©) ©) 0 1 z 1.14
*Chaenobryttus gulosus ©) 1 ) 4 1 6 6.82
‘Cichlasoma cyanoguttatum fe) 0 @) fe) 1 1 1.14
Total 15 7 20 27 19 88
Percent by Station 17.04 7.96 22.72 30.68 21.60 100.00
Rough Fish 15 6 17 22 17 77
Percent Rough Fish 100.00 85.71 85.00 81.48 89.47 87.50
*Game Fish (0) 1 3 5 2 11
Percent Game Fish 0.00 14.29 15.00 18.52 10.53 12.50
* Indicates Game Fish
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13.
Table 10. Grams of Fish Taken in Experimental Gill Nets
from Llano Grande Lake, November 1959.
Stations
Species 1 2 3 4 5 Total Percent
i ee en i: | ee fo
Lepisosteus spatula 15,648 ©) 25,600 21,150 @) 62,398 63.33
Lepisosteus productus 7,996 1,134 1,021 1,021 2,041 13,213 13.41
Dorosoma cepedianum 791 155 1,680 3,130 2,195 7,951 8.07
Cyprinus carpio 0 6,192 2,495 1,843 1,134 11,664 11.84
Ictalurus punctatus* @) fe) 2,295 90 ) 2,385 2.42
Micropterus salmoides* O re) ) ) 567 567 0.58
Chaenobryttus gulosus* ) 56 0 198 52 306 0.31
Cichlasoma cyanoguttatum 0) 0) (0) 0 35 35 0.04
Total 2h 435 7,937 33,091 27,432 6,024 98,519
Percent by Station 2h..80 7.65 33.59 27.84 6.12 100.00
Rough Fish 2h 435 7,481 30,796 27,144 5,405 95,261
Percent Rough Fish 100.00 99.26 93.06 98.95 89.72 96.69
Game Fish* ) 56 2,295 288 619 3,258
Percent Game Fish 0.00 0.74 6.94 1.05 10.28 3451
*I cates Game Fish
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Species
Lepisosteus spatula
Lepisosteus productus
Dorosoma cepedianum
Cyprinus carpio
Ictalurus punctatus
Micropterus salmoides
Chaenob tus gulosus
Cichlasoma cyanoguttatum
- Indicates only one fish.
Table
di.
from Llano Grande Lake, November 1959.
Lengths, Weights and "K" Factors of Fish Taken
Standard Length
Min.
590
450
120
260
150
100
Max.
gho
590
270
430
466
270
110
90
Avg.
810.64
500.77
190.04
346.43
253.50
270.00
101.67
90.00
Weight in Grams
Min. Max. Avg.
2,041 8,732 5,672.55
794 1,588 1,016.85
yo 459 0s«a:72. 24
465 2,495 1,484.00
90 2,041 596.25
- 567 567.00
hg 56 51.00
- 35 35.00
"K" Factor
Min. Max. Avg.
0.91 1.12 1.01
0.69 0.93 0.81
1.91 2.89 2.29
2.65 3.81 3.21
1.61 2.67 1.98
- 2.88 2.88
3.25 5.60 4.81
" 4.79 4.79
Rank
by No.
1 NO
Rank
by Wt.
=
oOo nrAy Nn WW
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15.
Table le. Success if Gill Netting on All Lakes in Terms
of Numbers and Pounds of Fish Caught.
Lake and Date Number Number Number Average Average Pounds Average Average
of of Feet of Fish Number of Number of of Fish Pounds of Pounds of
Nets of Nets Caught Fish Per Fish Per Caught Fish Per Fish Per
Set Set Net Foot of Net Net Foot of Net
Lake Casa Blanca, 16 2,000 hge 30.75 0.246 470.92 29.43 0.235
Oct. & Dec. 1959
Lake Fort Brown, 2 250 70 35.00 0.280 81.81 40.91 0.327
September 1959
Lake Llano Grande, 5 625 88 17.60 O.141 217.00 43.40 0.347
November 1959
Lake Campacuas, 3 375 23 7.67 0.061 23.03 7.68 0.061
November 1959