TPWD 1955 F-4-R-2 #157: Inventory of Species Present in Benbrook Lake, Benbrook, Texas
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STATE Texas
PROJECT NO. F-4-R-2, Job B-5
PERIOD June 1, 1954 - Oct. 31, 1955
SEGMENT COMPLETION REPORT
BY
ROBERT N. HAMBRIC
ASSISTANT PROJECT LEADER
TITLE
Inventory of Species Present in Benbrook Lake, Benbrook, Texas.
OBJECTIVES
To determine the species present and their relative abundance as well as the
ecological factors influencing their distribution.
HISTORY OF LAKE
Benbrook Lake is located in Tarrant County about 15 miles southwest of Fort
Worth, Texas. Closure of the dam was made September 29, 1952. The lake will
impound 3,769 surface acres of water at top of conservation pool which is 694 feet
above sea level. Rainfall has been light during the last few years over the entire
drainage area, which permitted the lake to fill to only about one-fcurth or one-
third of its normal capacity. The lake was stocked with 550,000 fish during 1953,
of which 370,000 were largemouth bass. Table 1 lists all fish that have been
stocked in Benbrook Lake by State and Federal Hatcheries. The impoundment was
closed to fishing in September 1953 and remained closed until June 1, 1954.
Fishing pressure was extremely heavy the first few days of the open season, but not
sO intensive there-after.
COLLECTING METHODS
The fish population was sampled each month by gill nets with meshes of 1 to 3
inches square measure. Periodic checks were also made with minnow seines measuring
30 by 6 feet with + inch mesh. The seined samples were preserved in 6 percent
formalin and taken to the laboratory for identification. The fish collected by gill
nets were worked to obtain their length, weight, gonadal development, and stomach
contents. A checklist of the fishes collected fran Benbrook Lake is recorded in
Table 2.
RESULTS OF SEINING COLLECTIONS
Seven seine collections were made to catch 621 specimens of fish numbering
19 species. Table 3 records the number of each species collected and the percentage
of the total number that it represents. Minnows and other forage fish were scarce
during the time that the predaceous species, mainly largemouth bass, were abundant.
(The beginning of the present survey coincided with the initial large bass harvest
from the lake, but work done immediately preceding the present study corroborates
the above statement. )
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Only two small shad were caught in the seine samples taken in July 1954,
indicating the spawn of that species had been heavily preyed upon and adequately
controlled when largemouth bass were abundant in the lake. It was further noticed
that fry and fingerling bass were also absent from the seine collections taken
during the summer and fall of 1954. If hatching had been successful the spawn
evidently had fallen prey to the larger fish. As the forage fish in the lake began
to multiply they were naturally taken in larger quantities in the seine collections.
Shad became so abundant during the fall of 1954 and in 1955 they accounted for
43.48 percent of all the specimens collected. This was a very high increase over
the 1.58 percent that they represented in the seine samples of the previous survey.
RESULTS OF NETTING COLLECTIONS
A total of 79 gill net sets were made from June 1954 through October 1955 to
produce 981 specimens representing 19 species. A tabulation of data from the net
collections is given in Table 4. The fish population in Benbrook Lake changed
from predominately game fish to mostly rough fish during the 17 month period of this
study. Table 5 offers a comparison of the present game fish and rough fish
populations of the lake with those of the previous survey.
The rapid increase in the rough fish population in Benbrook Lake has been an
interesting development and is due, in part, to the unique history of the lake
which immediately preceded this survey. A better understanding of the problem may
be had by a study of Table 6 which compares the results of the present and last
segments net collections by species, showing the percentage of the total catch by
both number and weight and the average "K" factor for each period. During the
time that the lake was closed to fishing the overcrowded bass were continuously
bunting for food. Nearly all types of animal life were heavily preyed upon, in-
cluding other bass. Although, they could not have existed forever under such
starvation conditions the bass were quite effective in devouring the spawn of all
fish before it had a chance to grow :off. Then when some 250,000 bass, plus many
fish of other species, were harvested from the lake during the first part of June
1954 it left the impoundment with insufficient predators to adequately control
the spawn of the remaining species. It was during the summer and fall of 1954
that the spawning of carp, shad and spotted sucker was so successful. The writer
believes itt is worthy of note that three of our better predators are not found
in the lake. These are the gars, flathead catfish, and white bass.
Six gill net sets made during June and mid-July, following the heavy fishe-
ing pressure in early June, produced only 24 specimens of which one-half were
large mature shad. Inspection of last segment's records revealed that each set
averaged 75 fish per net during that period of inventory. Large carp and shad
accounted Por 30 percent or more of the few fish caught from June to October. A
great many unmolested schools of small shad were seen on the surface for the first
time in October denoting a build up of food and a scarcity of predatory fish at
that time. Adequate samples of fish were caught in the nets from October 1954
through October 1955. Shad were the most abundant species captured, followed by
bass, carp, and spotted sucker. Many of the bass caught were probably those
stocked during the fall of 1954 as little evidence of a successful bass spawn was
found for that year. Internal inspection revealed that malnutrition had caused
many of the mature bass to reabsorb their eggs.
Carp and spotted suckers have multiplied fast and at various times each has
composed a major part of the net catch. White crappie were collected in limited
numbers from October until July. Most of them were small. Good catches of crappie
that weighed more than 8 ounces each were taken in August and September. There
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was no previous indication that this size-group of crappie were in the lake in
appreciable numbers. The crappie has increased from almost nothing to better than
8 percent of the total net catch.
The bullhead catfish population is still. high and during the last 17
months has more than doubled in representative percentage of the total fish netted.
The yellow bullhead was slightly the mcre abundant of the two species during the
previous study but was outnumbered 2 to 1 by the black bullhead in the present
survey. It seems possible that the yellow bullhead may disappear from the lake in
the future. The channel catfish population has remained relatively stable during
the past three years.
One of the more interesting developments of the lake has been a marked
change in the largemouth bass population. This species has decreased from a former
85 percent to the present 16 percent of the total net catch. Such a drop would
seem natura] when one considers the large harvest of bass taken from the lake in
1954. It is apparently better to have a smaller number of healthy bass in an
impoundment than to crowd the water with more fish than it can support. An
examination of the past records of the lake revealed some interesting changes in
the health and general condition of the bass. The extensive parasitism, mal-
nutrition, slow growth, and predation upon like species that was present during the
crowded condition was noticeably lacking in the present study. Neither was there
any indication of reabsorption of eggs by bass during the last spawning season,
and the increase in growth rate was accelerated when forage fish became abundant in
the lake. Bass that averased 104 ounces when the lake was closed to fishing in Sept-
ember averaged only 11¢ ounces when the lake was rédpened to fishing the following
June. During the next 17 months, while the lake was opened to fishing, the bass more
than doubled in weight for an average of 1.58 pounds for all fish netted.
The stomachs of the fishes were examined to note all conspicuous food
present. Many of the food items listed as unidentifiable fish remains were quite
possibly shad. Table 7 records the food items found and the frequency of their
occurrence for each species of fish studied.
By an inspection of the data collected during the past and present surveys
on Benbrook Lake it is noted that a rapid change in fish population, either in
types or numbers, may upset the lake balance causing it to fluctuate from one
extreme to another. It is recommended that further study be made of Benbrook Lake
in order to follow the development of that impoundment.
SUMMARY
1. Benbrook Lake was sampled with minnow seines and gill nets from June 1,
1954 to October 31, 1955.
2. A total of 621 specimens were collected by seines and 981 fish were taken
with nets.
3. Shad accounted for 22 percent of the total net catch as compared with less
than 3 percent found in the previous study.
4, Largemouth bass represented 16 percent of the fish netted as compared with
85 percent found in the previous survey.
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5. The fish population changed from predominately game fish to mostly rough
fish during the 17 month period of this survey.
6. Bass grew much faster after the lake was opened to fishing.
7. Malnutrition, parasitism, and the reabsorption of eggs was not present
after the crowded game fish population of the lake was alleviated.
8. A rapid change in fish population, either in types or numbers, may upset
the lake balance causing it to fluctuate from one extreme to another.
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Table 1. Hatchery Stocking of Fish in Benbrook Reservoir, May 1, 1953 ~- October 31, 1955.
Species Totals
Channel Catfish (Ictalurus
Largemouth Bass (Micropterus salmoides)
Warmouth Bass (Chaenobryttus coronarius )
Redear Sunfish (Lepomis microlophus)
Bluegill Sunfish (Lepomis macrochirus)
Longear Sunfish (Lepomis megalotis)
Yellowbelly Sunfish (Lepomis auritus)
White Crappie (Pomoxis annularis)
Black Crappie (Pomoxis nigromaculatus )
109 , 000 191,525
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Table 2.
Checklist of Fish Species from Benbrook Lake, Texas, 1954-55.
Common Name
Scientific Name
e
° °
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09 OANA WW FWY
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25.
Gizzard Shad
River Carpsucker
Grey Redhorse
Spotted Sucker
Carp
Redfin Shiner
Brazos River Shiner
Blacktail Shiner (Spottail)
Red Shiner (Redhorse)
. Parrot Minnow
. Fathead Minnow
Southern Channel Catfish
. Black Bullhead
» Yellow Bullhead
. Blackstripe Topminnow
. Gambusia
. Largemouth Black Bass
Warmouth
- Green Sunfish
. Redear Sunfish
- Bluegill Sunfish
Yellowbelly Sunfish
- White Crappie
Dusky Darty
Logperch
Dorosoma cepedianum
Carpiodes carpio
Moxostoma congestum
Minytrema melanops
Cyprinus carpio
Notropis umbratilis
Notropis brazosensis
Notropis venustus
Notropis lutrensis
Pimephales vigilax
Pimephales promelas
Ictalurus punctatus
Ameiurus melas
Ameiurus natalis
Fundulus notatus
Gambusia affinis
Micropterus salmoides
Chaenobryttus coronarius
Lepomis cyanellus
Lepomis microlophus
Lepomis macrochirus
Lepomis auritus
Pomoxis annularis
Hadropterus scierus
Percina caprodes
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ic
Table 3. Results of Seining Collections by Number of Each Species, Benbrook Lake, Texas, 1954-55.
Species
Gizzard Shad
Grey Redhorse
Spotted Sucker
Redfin Shiner
Brazos River Shiner
Blacktail Shiner (Spottail)
Red Shiner (Redhorse)
Parrot Minnow
Fathead Minnow
Blackstripe Topminnow
Gambusia
Largemouth Black Bass
Green Sunfish
Redear Sunfish
Bluegill Sunfish
Yellowbelly Sunfish
White Crappie
Dusky Darter
Logperch
Number Collected
Percent of Total
100.00
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8.
Table 4. Tabulation of Data From Gill Net Collections From Benbrook Lake, June 1954 Through October 1955.
Species Number Percent of Pounds Percent of Avg. Weight No. of Fish
Caught Total Number Caught Total Weight in Pounds Per 100' Net
Gizzard Shad 218 22.22 79.39 9.83 436 2.73
Carpsucker 21 2.14 66.47 8.23 3.17 .26
Gray Redhorse 1 2 LO (5 .O9 (5 OL
Spotted Sucker 132 13.46 75.93 9.40 258 1.66
Carp 145 14.78 157.30 19.48 1.08 1.82
! Channel Catfish 25 2.56 48.05 5.95 1.92 "431
: Y. Bullhead 53 5.40 25.09 Se 1. oT . 66
| B. Bullhead 91 9.28 35.94 WAS 239 1.14
L. M. Bass 156 15.90 2h9 86 30.95 1.58 1.6
Warmouth 2 »20 1.30 .16 265 .03
Green Sunfish 1 é10 237 205 «37 OL
Y. B. Sunfish 2 220 42 806 221 .03
Bluegill Sunfish 53 5.40 20.46 2.54 £39 .66
White Crappie 81 8.26 46.01 5.70 «57 1.02
Total 981 100.00 807.34 100.00
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9.
Table 5. A comparison of the Game and Rough Fish Caught by Gill Nets in Benbrook Lake.
June 1953 June 1954 Percentage Change
Netting Collections through through
May 1954 October 1955 Increase Decrease
Total No. of Specimens Caught —
* Total Wt. of Specimens Caught
Average Wt. Per Specimen 17.20
**¥Total Weight of Game Fish
Total Wt. of Rough Fish 129.68
Total No. of Game Fish
Total No. of Rough Fish 176.57
Ave. Wt. Per Game Fish 52.67
Avg. Wt. Per Rough Fish
Percent Game Fish By Number
Percent Rough Fish By Number 516.47
Percent Game Fish By Weight
Percent Rough Fish By Weight 367.15
* Weight in pounds
** Catfishes, included in game fish
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LO.
Table 6. Results of the Current Netting Collections from Benbrook Lake as Compared with Collections of the
Preceding Study.
June 1953 - May 1954 June 1954 - October 1955
Percentage of Total Catch Percentage of Total Catch
Species By Number By Weight Avg. "K" Factor By Number By Weight Avg."K" Factor
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River Carpsucker
Gray Redhorse
Spotted Sucker
Carp
Southern Channel Catfish
Yellow Bullhead
Black Bullhead
Largemouth Black Bass
Warmouth
Green Sunfish
Yellowbelly Sunfish
Bluegill Sunfish
White Crappie
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ll.
Table 7. Frequency of Occurrence of Food Items from Fish Collected By Gill Nets, Benbrook Lake, June 1954
Through October 1955.
Species Unidentifiable Insects Algae and Mussels No. of Fish
Fish Remains Vegetation Examined
Largemouth Black Bass 18 7 1 128
White Crappie 3 36 1 3 78
Southern Channel Catfish 8 2 3 7 25
Black Bullhead 9 2 15 38
Yellow Bullhead 1 6 1 20
Bluegill Sunfish 1 6 12
Warmout h L e