TPWD 1960 F-4-R-7 #616: Resurvey and Appraisal of Several Public Waters in Region 4-B
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Report of Fisheries Investigations
Resurvey and Appraisal of Several Public waters in‘ngion.h-B
by
LSQnard D. Lamb
Project Leader
Dingell—Johnson Project F-h—R—7, Job 3-261
'Novembsr l, 1959 - Octdber 31, 1960
H. D. Dodgen - Executive Secretary
Texas Game and Fish Commission
Austin, Tsxas
Marion Tools Ksnnsth C. Jurgens and William E. Brown
Cecrdinator Assistanfi Coordinators
A B S T R A C T
Seven lakes in Region h-B were resurveyed. These include
Lakes Bcnbrook, Eagle Mountain, Fincastle, Fort Parker, waco,
Whitney, and worth. The results of the resurvey work on Fort
Parker was included in the completion report for Project F-lfi-D—h,
Jdb 16a2h. The results of resurvey‘work on Fincastle Lake and Lake
Whitney have been included in completion reports for Project F-h-R-T,
Jdbs E—h and E-7.
An abstract and discussion of each lake, including population
changes, is made separately.
Segment Completion Report
State of TEXAS
Project No. F—h-R-T Name: ”Fisheries Investi ations and Surve s
of the waters of Region E-B.
Job No. I _ B-26 Title: Resurve and A' raisal of Several
Public waters in Region E-B.
Period covered: ' ' November 12 1959 - October 312 1960
OBJECTIVES
To determine the present status of waters and fish populations which have been
previously surveyed in Project F-h-R.
PROCEDURE
Certain previously surveyed waters in Region h-B were revisited and seine or net
checks made. The data collected was examined and compared to that collected during
the previous survey to determine any changes that might have occurred.
Netting or seining was done at the site of previously established stations if
water conditions permitted. Net colleCtions were made with nylon gill nets 100 feet
by 8 feet with l%-inch mesh. water analysis was not attempted because of the diffi-
culty encountered in keeping fresh reagents. Changes in ecological conditions were
noted as were changes in populations.
The waters that were revisited during this segment were Lakes Benbrook, Eagle
Mountain, Fincastle, Fort Parker, waco, Whitney, and WOrth.
The results of the resurvey of Fort Parker Lake has been included in completion
report for Project F-l5-D-h, Job l6a2h.i The results of resurveys on Fincastle Lake
and Lake Whitney have been included in completion reports for Project F—h-R-T, Jabs
E-h and E-7. '
Seining was made difficult by rises in water level that made the previously
cleared seining beaches unfit for use..
Prepared by Leonard D. Lamb Approved by 2 32W l/M'é
Project Leader Dire tor Inland Fisheries Division
Date February 102 1261
-2-
Lake Benbrook
ABSTRACT
The population of_Benbrook Lake showed a definite game fish dominance in the 1953-
l95h netting with.89 percent game fish. Largemouth bass,_Micropterus salmoides, com-
posed 8h.77 percent of this total. Rough fish became dominant in 195u-1955 when bass
”dropped to 15.9 percent. The rough fish dominance continued in 1955-1956 when spotted
suckers, Minytrema melanops, provided 51.h8 percent of the catch and white crappie,
:_Pomoxis annularis, composed 21.39 percent. Game fish were 29.50 percent of the total
“ catch. The 1958-59 not catch showed a marked change when game fish provided 63 percent
of the catch. Channel catfish, Ictalurus punctatus, accounted for 30.hh percent.
The 1959-1960 netting showed a return to rough fish dominance with rough fish
comprising.69.l3 percent. Gizzard shad, Dorosoma ce edianum,-made up 62.67 percent
of the catch and white crappie, the most numerous game species, provided 11.73 percent.
DISCUSSION AND FINDINGS
Lake Benbrook is.a flood control and water conservation impoundment on the Clear
Fork of the Trinity River near Fort Worth, Texas. The dam was constructed by the U.S.
Corps of Engineers and was closed September 29, 1952, but lack of rainfall delayed
filling until 1957.
Changes in population trends have been marked (Table 1). The l953-l95h net
catches were 89.07 percent game fish, with largemouth'bass making up 8h.77 percent 0’
that total. The l95h-1955 net catch contained only 15.9 percent bass, while gizzard
shad proved to be the most numerous species with 22.22 percent. Spotted suckers com-
prised lh.78 percent to be the third species in abundance.“ The 1955—1956 netting
was dominated by the spotted suckers, with 51.h8 percent, while game fish made up
29.5 percent of which 21.39 percent was white crappie. Gizzard shad provided 11.75
percent. There was no netting on this lake in 1957, but the l958~l959 netting showed
a marked change. Game fish then made up 63 percent of the total with channel catfish
providing 30.hh percent. Spotted suckers, gizzard shed, and largemouth bass followed
with 18.u7, 17.39, and 16.30 percent respectively.
The 1959-1960 netting showed still further rough fish dominance but spotted
suckers did not appear in the catch (Table 2). Gizzard shad made up 62.67 percent of
the 69.13 percent contributed by rough fish. White crappie, largemouth bass, and
bluegill sunfish,_Lepomis macrochirus, provided 11.73, 8.38, and 7.65 percent re—
spectively. Carp, Cyprinus carpio, and river carpsuckers, Carpiodes carpio, appeared
in thegcateh with carp providing 5.27 percent of the catch. This increase in the
relative abundance of rough fish is not unexpected since this lake is now eight years
old and appears to be following the usual pattern of reservoirs in this area.
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Eagle Mountain Lake
ABSTRACT
The dominance of game fish in the 1955-1956 net collections was not continued in
subsequent nettings. Rough fish provided 78.57 and 57.25 percent of the 1958—1959
and 1959—1960 net collections, respectively.
Gars, Lepisosteus sps., and gizzard shad are the most numerous rough fish while
white bass, Roccus chrysops, and white crappie provided the highest percentages of
the game species.
Gar make up the majority of the weight of the catch and it is believed that much
benefit could be obtained from a satisfactory means of gar control.
DISCUSSION AND FINDINGS
Eagle Mountain Lake is located on the west Fork of the Trinity River between
Lake Worth and Lake Bridgeport. The dam was completed in 1932 as a water supply for
the City of Fort Worth, Texas.
A fishery survey made in 1955~l956 showed a game fish dominance in the net catches.
Game species made up 67.67 percent of the catch with white bass providing h8.99 per—
cent.
In 1958-1959, a recheck was made and the results of netting indicated that the
rough fish were predominant as they made up 78.57 percent of the total with gars and
gizzard shad accounting for h1.h3 and 25.72 percent respectively. White bass had
been the dominant species during the previous netting but provided only h.29 percent
of the 1958-1959 catch (Table 3).
Rough fish continued to dominate the not catch in 1959-1960 but to a smaller
degree. Gizzard shad comprised over half of the total rough fish percentage with
33.59 percent. Rough fish comprised a total of 57.25 percent of the not catch.
White bass again were the most numerous game fish in the catch with 25.19 percent.
White crappie were in fourth position with 11.46 percent just behind longnose gar,
Lepisosteus osseus, with 17.56 percent (Table h).
The gars continue to be prominent in the fish population of this lake. They pro-
vided an even greater percentage of the total poundage than they do of the numbers.
A satisfactory means of control for these species should be of great benefit to this
and many other lakes.
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Lake WOrth
Lake Worth was impounded in 1912 and was the first of a chain of three water sup-
ply lakes for Fort Werth, Texas. It is located on the West Fork of the Trinity River
above the confluence with the Clear Fork.
Early gill net collections showed a game fish dominance when 57.02 percent of the
catch were game species. White crappie provided H3.80 percent. 'This predominance of
game fish continued in 1958-1959 when'game species made up 75.61 percent of which blue-
gill sunfish and largemouth bass provided 36.59 and 12.20 percent respectively. The
1959-1960 nettingeshowed still further overbalance in favor of game species when net
catches showed 86.07 percent with white crappie and white bass making up h8.36 and
22.13 percent respectively. '
DISCUSSION AND FINDINGS
Lake Worth was constructed in 1912 to provide a water supply for the City of Fort
Worth, Texas. It is the first of a chain of three lakes on the West Fork of the
Trinity and is located about six miles above the confluence with the Clear Fork.
Gill net collections made during 1955—1956 showed game species to dominate the
catch with white-crappie providing h3.80 percent of the 57.02 percent total. Gizzard
shad were the most numerous rough fish present with 23.h7 percent. The 1958-59 net
collections were also dominated by game fish as-bluegill sunfish and largemouth bass
provided 36.59 and 12.20 percent respectively of the 75.61 percent that were game
fish species (Table 5). The 1959-1960 netting was overbalanced still further in favor
of the game fish species. They provided 86.07 percent of the total catch. White
crappie made up h8.36 percent followed by white bass with 22.13 percent. Gizzard
shad were the most numerous rough species with 5.7% percent of the total (Table 6).
Lake WOrth is located within the Fort Werth City limits and is almost completely
surrounded by homes. The residents of these homes fish almost constantly with trotn
lines and set lines, along with artificial lures or minnows when weather conditions
are favorable. Many large flathead catfish, Eylodictus olivaris, are taken from this
lake by trotline fishermen.- '