TPWD 1963 F-5-R-10 #862: Fisheries Investigations and Surveys of the Waters of Region 1-B: Job No. B-32 Fisheries Reconnaissance
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JOB COMPLETION REPORT
As required by
FEDERAL AID IN FISHERIES RESTORATION ACT
Federal Aid Project No. F-5-R-10
FISHERIES INVESTIGATIONS AND SURVEYS OF THE WATERS OF REGION 1-B
Job No. B-32 Fisheries Reconnaissance
Project Leader: Lawrence S. Campbell
J. Weldon Watson
Executive Director
Parks and Wildlife Department
Austin, Texas
Marion Toole Eugene A. Walker
D-J Coordinator Director, Program Planning
October 24, 1963
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ABSTRACT
Fish populations were examined for 15 public reservoirs and 5 major
streams. Sampling of fish populations included analysis of data for 8,768
fish captured in 349 gill net collections and examination of thousands of
fish captured in seining collections. Reconnaissance served primarily to
sample public waters to determine major changes in relative abundance. This
work was also instrumental in providing data that is the basis for biologically
sound fish harvest regulations; that justifies and is the basis for affording
priority for management planning and specifications; that partially evaluates
the results of previous management; that maintains knowledge of the distribution
of rare and/or diminishing species and that provides a better understanding of
ecological phenomena that influences fish production. Surveys for management
justification and planning were carried out for Lake Nasworthy, San Angelo
Reservoir, Oak Creek Reservoir, New Winters Lake, Old Ballinger Lake, and
Valley Creek Reservoir. Studies to evaluate previous management efforts were
carried out at Lake Balmorhea, Lake Ascarate, Oak Creek Reservoir, Lake Sweet-
water, Champion Creek Reservoir, and Mountain Creek Reservoir. Studies to
determine ecological influences, game fish production, and sound harvest
regulations were conducted at Red Bluff Reservoir, Imperial Reservoir, Lake
Colorado City, Devils Lake, the lower Pecos River and portions of the upper
Colorado River.
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JOB COMPLETION REPORT
State of Texas
Project No. _F-5-R-10 Name: Fisheries Investigations and Surveys of the
Waters of Region 1-B .
Job No, B-32 Title: Fisheries Reconnaissance
£isttet tS ee
Period Covered March 1, 1962 - February 28, 1963
Objectives:
To conduct limited investigations to obtain current information concerning
gross changes in fishing conditions and factors influencing fish populations.
Procedures:
1. Fish populations were examined for 15 public reservoirs and 5 major
streams. Population sampling included analysis of data for 8,768 fish captured
in 349 gill net collections, and for many thousands of fish captured in seining
collections.
2, Reconnaissance was primarily directed toward population sampling
required in determining major changes in relative abundance and balance between
desirable and undesirable species of fish produced. Data indicative of changes
in condition of principal species were obtained. °
3. Limited investigations were carried out to obtain data necessary for
evaluation of management work, to maintain knowledge of expanding populations
of problematic or exotic fish, or to determine the continued existence of
diminishing species. Other study was designed to provide data of fish survival
in polluted areas, and to obtain knowledge of species or circumstances not
previously investigated.
4, Where pertinent, major changes in ecological conditions, water quality,
turbidity, plant life, and water usage were investigated.
5. A point of reference for comparing fluctuations in water levels was
established on all waters visited.
6. Lesser investigations included making suitable inquiries to determine
land usage or changes in land usage for watersheds, sources of pollution, and
other changes in influences of importance.
7, Shoreline usage and accessibility, public ingress and egress, and
conveniences such as launching ramps, toilets, picnic areas, and fish attractors
were determined.
8. Where practical, fishing success and fishing pressure were investigated
by cursory examination of spot checks of fish harvest composition.
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9. Examination of reconnaissance data was made to determine if more
elaborate resurvey of the concerned waters was required. This examination
subsequently resulted in extensive study of four major waters.
Organization and Limitations of Report
For coherence, reconnaissance work carried out is divided into two major
categories. The essential difference between categories under which specific
work is discussed is motive for pursuing the effort and the amount of work re-
quired for its accomplishment. For this reason, reconnaissance effort for a
specific body of water may be of secondary classification under this report and,
as a result of work and findings, be of primary classification in the future,
Much unfinished work is of this status,
Reconnaissance efforts were required to determine financial practicality
and other justification for management planning. These investigations were lengthy
and thorough and are delegated primary classification, Such multipurpose work
is the means of setting up long-range management plans that ultimately may
involve successive management of several bodies of water. These waters are
grouped for management consideration and are located within predetermined day-
use areas. Data obtained provided: (1) determination of logical succession
of tasks and procedures for management of waters grouped; (2) the determination
of specific techniques required for included waters; (3) background data
essential to future valuation of the pre-management and post-management fishery
and (4) data contributive to the expansion of knowledge of population dynamics
and of life histories of various species of fish.
Less extensive reconnaissance is designated as secondary reconnaissance
effort. These investigations were primarily concerned with providing data for
a single body of water or for a specific habitat within a single body of water.
These studies also provide data to evaluate the results of previous management
work, to record changes in production brought about by changing circumstances
or conditions, for providing a basis for harvest regulations, to maintain
knowledge of the rate of expansion of specific fish, to determine the status
of diminishing species, to ascertain the influence of pollution, to attempt
to establish rate of growth or spawning requirements for little known species,
and to determine distribution of introduced or exotic species. An outline of
work completed and objectives is as follows:
Primary Reconnaissance Surveys
A. Pre-management reconnaissance and management planning.
1. Lake Nasworthy and associated waters of the Concho River (justification)
for proposed management, evaluation data, population dynamics).
2. San Angelo Reservoir and portions of the North Concho River (area
planning for management, game fish production, factors influencing
harvest).
3. Oak Creek Reservoir and connecting portions of Oak Creek
(justification for management, evaluation of management,
population dynamics),
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4, Imperial Reservoir (management planning for the Pecos River watershed,
basis for harvest regulations, population dynamics, uncommon
influences).
Secondary Reconnaissance Surveys
A. Reconnaissance to evaluate previous management.
1. Lake Balmorhea
2. Mountain Creek Reservoir
3. Lake Sweetwater
4. Lake Ascarate
5. Champion Creek Reservoir
B. Reconnaissance to provide specific data.
1. Red Bluff Reservoir (management planning, population dynamics,
harvest regulations).
2. Lake Colorado City (uncommon phenomena and its influence on fish
produced, harvest regulations).
3. New Winters Lake (management planning, harvest regulations).
4. Old Ballinger City Lake (management planning, harvest regulations,
influence of pollution).
5. Valley Creek Reservoir (management planning, harvest regulations).
6. Devils Lake (production data, harvest regulations, study of little
known species).
7. Lower Pecos River (diminishing species, pollution influence, harvest
regulations).
8. Upper Colorado River (minnow production and influences).
Note: The other three streams referred to in item 1 of procedures were Elm Creek,
North Concho River, and the Concho River below Lake Nasworthy. These
investigations were carried out in conjunction with study of reservoirs.
Results:
References are made throughout this report to a number of species of fish.
The following checklist has been prepared to assure correct identification.
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spotted gar -------------------------------- Lepisosteus oculatus
alligator gar ------------------------------ L. spatula
longnose gar ------------------------------- L. osseus
gizzard shad ------------------------------- Dorosoma cepedianum
Mexican tetra ------------------------------ Astyanax mexicanus
smallmouth buffalo ------------------------- Ictiobus bubalus
river carpsucker --------------------------- Carpiodes carpio
gray redhorse ----~------------------------- Moxostoma congestum
blue sucker ------------------- mmm mania Cycleptus elongatus
CALP SHeeSSS SSeS ine eee n nee = Serres Cyprinus carpio
golden shiner --------------- oS SEE S See Notemigonus crysoleucas
blacktail shiner --------------------------- Notropis venustus
red shiner --------------------------------- N. lutrensis
roundnose minnow --------------------------- Dionda episcopa
plains minnow ------------------------------ Hybognathus placita
bullhead minnow ---------------------------- Pimephales vigilax
walleye ------------------------------------ Stizostedion vitreum
channel catfish ---------------------------- Ictalurus punctatus
blue catfish ------------------------------- i. furcatus
yellow bullhead ---------------------------- i. natalis
black bullhead ----------------------------- i. melas
flathead catfish --------------------------- Pylodictus olivaris
plains killifish --------------------------- Fundulus kansae
mosquitofish ------------~------------------- Gambusia affinis
tidewater silverside ----------------------- Menidia beryllina
white bass --------------------------------- Roccus chrysops
Guadalupe bass ----------------------------- Micropterus treculi
largemouth bass ---------------------------- M. salmoides
warmouth bass ------------------------------ Chaenobryttus gulosus
green sunfish ------------------------------ Lepomis cyanellus
spotted sunfish ---------------------------- L. punctatus
redear sunfish ----------------------------- L. microlophus
bluegill ----------------------------------- L. macrochirus
redbreast sunfish -------------------------- L. auritus
longear sunfish ---------------------------- L. megalotis
white crappie ------------------------------ Pomoxis annularis
black crappie ------------------------------ P. nigromaculatus
logperch ----------------------------------- Percina caprodes
freshwater drum -----------~----------------- Aplodinotus grunniens
Rio Grande perch ~-------------------------- Cichlasoma cyanoguttatum
southern flounder -------------------------- Paralichthys lethostigma
red drum ----------------------------------- Sciaenops ocellata
Primary Reconnaissance
A. Pre-management reconnaissance and management planning.
Lake Nasworthy was formerly the primary source of municipal water for San
Angelo, Texas. The lake is 6.5 miles southwest of the city and impounds the
Middle and South Concho Rivers. Within the year a major flood control-irrigation
project has been completed above Lake Nasworthy. A Bureau of Reclamation project,
Twin Buttes, will be capable of impounding 600,000 acre feet and of expanding
to 23,000 acres. In the future, water from Twin Buttes will be released into
Lake Nasworthy. The lower structure, acting as the control reservoir, will
divert flow either into a canal system where it will be transported to irrigated
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farm lands located west of the city, or into the old stream channel below the dam
where it enters the city water supply system. The basin area for the new reservoir
and most of Twin Buttes watershed has been chemically treated to reduce problematic
fish. (See completion report for Job 16a39, Project F-14-D-6). Previous survey
work for Lake Nasworthy indicated river carpsuckers, carp and other problematic
species have dominated past fish production. In order to continue the watershed
renovation program to its logical limits a thorough reconnaissance of Lake
Nasworthy and its associated waters was required. Fifty-four gill net collections
were made from the lake and the stream areas below the dam. Approximately three-
fourths (74.46 per cent) of 2,028 fish captured in 15,025 feet of gill nets were
problematic species. River carpsuckers and gizzard shad represented 62.62 per
cent of the total catch. The next most abundant species was white crappie making
up 8.92 per cent of fish captured. One-third of these (68 of 181) were classified
as nonutilizable. Less than 18 per cent of fish taken were considered to possess
utility.
During this period of study the lake receded from 12,340 acre feet storage to
2,400 acre feet. This has resulted in relatively high fishing success due to
crowding of game fish present. In order to proceed with management to its logical
conclusion and so that Lake Nasworthy could be improved at minimum costs, it was
recommended to responsible authorities that existing fish (with the exception of
salvagable game fish) be drastically reduced or eradicated. This recommendation
was endorsed by the Concho Bass Club, the Lake Advisory Board and the City
Commission. The work will be carried out during the summer of 1963.
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Table l
Netting locations and feet of net per location for reconnaissance
of Lake Nasworthy and associated waters - January 1-31, 1963
TOTO
Location No. Nets No. Feet of Net
et CON, Feet of Net
Red Bluff Slough 8 1,250
South Concho River 14 1,975
Spring Creek 14 1,975
Middle Concho River 14 1,975
Lower Concho River
(Country Club, Ben Ficklin,
Lone Wolf) 24 3,450
Lake Nasworthy 19 4,400
Totals 93 15,025
err nk
Table 2
Analysis of utilizable game fish taken from Lake Nasworthy
and associated waters
January 1-31, 1963
Per cent Per cent
of total Total of total
catch by weight catch by Average
Species No. number pounds weight weight
largemouth bass 83 4.09 274.05 7.15 3.30
white bass 104 5.13 80.34 2.10 0.77
yellow bullheads 1 0.05 0.65 0.02 0.65
channel catfish 60 2.96 94.53 2.47 1.58
flathead catfish 4 0.20 21.56 0.56 5.39
white crappie 113 5.57 67.96 1.77 0.60
Subtotal 365 18.00 539.09 14.07
eee
Total game fish 518 25.54 556.19 14.53
_ -Orrc s—— eeeeeeee
Total problematic
fish 1,510 74.46 3,274.40 85.47
enn
Total catch 2,028 100.00 3,830.59 100.00
SSS
Minimum weights of fish regarded as having utility - catfish - 200 grams, all
others 100 grams.
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=12=
Table 8
Stomach content of fish taken from Lake Nasworthy and associated waters
January 1-31, 1963
Number Frequency
Species Number with Food of
Examined Food Items Occurrence
largemouth bass 20 14 gizzard shad 11
fish remains 3
white bass 98 48 gizzard shad 21
fish remains 26
channel catfish 28 12 gizzard shad 8
fish remains 2
algae 1
pecan 1
white crappie 90 47 gizzard shad 12
fish remains 33
bluegill 2 0)
freshwater drum 4 1 gizzard shad 1
TT
Totals 242 122
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ke
San Angelo Reservoir is a flood control structure constructed and operated
by the U. S. Corps of Engineers. The dam is adjacent to the northwestern
residential section of San Angelo. At conservation pool the reservoir retains
119,188 acre feet and covers 5,456 acres. Under a change in water usage practices
San Angelo Reservoir is presently the primary source of water for San Angelo,
Currently the reservoir has 52,730 acre feet of water and is about 31,000 acre
feet below dead storage. The lake has receded continuously for four years. In
conjunction with management planning for Lake Nasworthy a survey of San Angelo
Reservoir and portions of the North Concho River was carried out. This was done
to provide assurance of public fishing while management was being carried out
for the smaller lake and for setting up long-range management plans, Thirty gill
net collections captured 707 fish, and 2 seining collections captured over 830
individuals. Less than 18 per cent of fish captured were usable game fish.
Approximately 77 per cent of fish taken were problematic species. River carp-
suckers made up 68.03 per cent of the total number of fish netted and 55.30
per cent of the weight of fish captured. White bass were the most numerous game
species, but largemouth bass, with an average weight of 5.64 pounds, were
probably the greatest fishery asset. Failure to capture smaller largemouth
bass, channel catfish, and white bass is interpreted as being indicative of
failure of those species to reproduce. Gill netting collections from the Concho
River below the reservoir resulted in capturing 96.67 per cent problematic
species. Fishing results expressed in fish per man hour have been low, but
skillful anglers consistently record sizeable catches of largemouth bass and
white bass. The crowding of fish through the continued reduction of the lake
volume is of significance in aiding anglers,
--- Page 16 ---
-[4-
Table 9
Per cent composition by weight and mean weight of fish taken from
San Angelo Reservoir
January 1-31, 1963
EE —
Total Per Cent
Per Weight by Weight
Species Number Cent Pounds Pounds Mean Weight
largemouth bass 40 5.66 225.56 14.94 5.64
white bass 66 9.34 120.19 7.96 1.82
channel catfish 18 2.55 33.76 2.24 1.88
flathead catfish 1 0.14 50.13 3.32 50.13
white crappie 30 4.24 15.50 1.03 0.52
bluegill 4 0.57 0.26 0.02 0.07
Subtotal 159 22.50 445.40 29.51
smallmouth buffalo 9 1.27 114.38 7.57 12.71
carp 29 4.10 86.69 5.74 2.99
river carpsuckers 481 68.03 835.13 55.30 1.74
black bullhead 1 0.14 0.65 0.04 0.65
freshwater drum dL, 0.14 1.13 0.07 1.13
longnose gar 2 0.28 12.81 0.85 6.40
gizzard shad 19 2.69 2.85 0.19 0.15
golden shiner 1 0.14 0.14 0.01 0.14
gray redhorse 5 0771 10.88 0.72 2.18
Subtotal 548 77.50 1064.66 70.49
Totals 707 100.00 1510.06 100.00
Table 10
Analysis of utilizable game fish taken from San Angelo Reservoir
January 1-31, 1963
eee
Per Cent of Total Per Cent of
Total Catch Weight Total Catch Average
Species Number by Number Pounds by Weight Weight
largemouth bass 40 5.66 225.56 14.94 5.64
white bass 65 9.20 119.98 7.95 1.85
channel catfish 15 2.12 32.90 2018 2.19
flathead catfish il 0.14 50.13 3.32 50.13
white crappie 6 0.85 6.71 0.44 1.12
Subtotal 127 17.97 435.28 28.83
Total game fish 159 22.50 445.40 29.51
Total problematic
fish 548 77.50 1064.66 70.49
Total catch 707 100.00 1510.06 100.00
Minimum weights of fish regarded as having utility - catfish 200 grams, all
others 100 grams.
--- Page 17 ---
Table 11
A comparison of utilizable game fish with problematic fish from
North Concho River
January 1-31, 1963
Per Cent of Total Per Cent of
Total Catch Pounds Total Catch Average
Species Number by Number Weight by Weight Weight
largemouth bass 1 83 3.06 4.67 3,06
channel catfish 2 1.67 5.19 7.92 2.50
Subtotal 3 2.50 8.25 12.59
river carpsuckers 29 24.16 45.31 69.18 1.56
freshwater drum 1 83 1.13 1.72 1.13
gizzard shad 87 72.51 10.81 16.51 a2
Subtotal 117 97.50 57.25 87.41
Total 120 100.00 65.50 100.00
ON
Minimum weights of fish regarded as having utility - catfish 200 grams, all others
100 grams.
10 Bem
Table 12
Composition by number of fish taken by rotenone sampling of
North Concho River
January 1-31, 1963
Species Number Per Cent by Number
channel catfish 2 2.77
bluegill 6 8.34
green sunfish 2 2.77
longear sunfish 5 6.95
warmouth bass 2 Zed
Subtotal 17 23.60
river carpsucker 2 2.77
freshwater drum 1 Ladd
gizzard shad 32 44.45
golden shiner 2 2.77
Subtotal 37 51.38
blacktail shiners 4 5204
bullhead_ minnows 14 19.45
Subtotal 18 25.02
Total 72 100.00
a
--- Page 18 ---
-16-
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--- Page 20 ---
-18-
Table 15
Stomach contents of fish taken from San Angelo Reservoir January 1-31, 1963
No. stomachs Number Frequency of
Species Examined With Food Food items Occurrence
largemouth bass 24 14 unidentifiable 7
fish remains
gizzard shad 6
white bass 1
white bass 70 54 unidentifiable 22
fish remains
gizzard shad 29
white crappie 26 4 unidentifiable 2
fish remains
gizzard shad 2
bluegill 2 0
black bullhead 1 0
freshwater drum 1 ()
Totals 124 72
--- Page 21 ---
=19=
Oak Creek Reservoir is located three miles southeast of Blackwell, Texas,
on the Nolan-Coke county line. At spillway level the reservoir contains
52,900 acre feet of water and covers 1,500 acres. The lakes waters are normally
clear, and the basin topography is excellent for fishing. Practically no
run-off has entered the lake in the past two years. Reconnaissance work com-
pleted under project F-5-R-9 indicated that due to a continued recession of the
lake, problematic species had increased from less than 50 per cent in 1960 to
over 80.95 per cent in January of 1962. The city of Sweetwater and other
municipalities who own the reservoir requested that something be done to improve
fishing. In compliance with this request a reconnaissance was made of the lake.
This pre-treatment sampling consisted of eighteen gill net sets that captured
619 fish. Of the fish captured not less than 89.91 per cent by weight and
75.25 per cent by number were undesirable. The capture of over 34 fish per
net is significantly higher than average netting success. It was originally
proposed to attempt eradication of fish life. However, permission from State
health authorities to use toxaphene for this purpose could not be obtained.
The cost of using rotenone in a total kill effort was too great. An alternate
plan was selected that provided for a drastic reduction of existing fish by
employing a contour type treatment. Between June 14 and June 19, 1962, Oak Creek
Reservoir was treated with 8,800 pounds of 5.67 per cent powdered rotenone. The
shallower areas of the lake, those less than 8 feet deep, were treated with
sufficient chemical to provide an immediate concentration of 1.47 parts per
million. The deeper areas were treated in such a manner as to achieve an
immediate dosage of .099 parts per million. The resulting destruction of
fish was estimated as approximately 68,000 pounds. For further data see job
completion report 16a36, Project F-14-D-6.
To evaluate the results of this work 44 gill nets were set after the
treatment. A total of 560 fish were captured, an average of 12.72 fish per
net, or about 30 per cent of the pre-treatment catch. The primary problematic
species, river carpsuckers, were reduced from about 24 per cent of the pre-
treatment catch to about 13 per cent of the post-treatment sample. Gizzard
shad were reduced from 52 per cent of the pre-treatment sample to about 11 per
cent of the post-treatment catch. Largemouth bass increased from about .65
per cent in June to 20.66 per cent in October. An examination of creels also
indicated a marked increase in fishing success during the period. The final
results of this work will depend upon spring run-off that should refill the
reservoir. For specific data see tables 16 through 20.
--- Page 22 ---
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--- Page 27 ---
-25-
Imperial Reservoir is an irrigation control reservoir for Red Bluff Power
and Water District. This playa lake, whose natural capacity was increased by
construction of a dam, is located in a bend of the Pecos River about 10 miles
west of the town of Imperial in Reeves County. Water is diverted from the
Pecos and enters the reservoir through a canal. Releases are as irrigation
demands. Flow of the upper Pecos is controlled by Red Bluff Reservoir and
several reservoirs in New Mexico. The reservoir is primarily for irrigation
but is of unusually high recreational importance because of its geographical
location. Imperial is unique in the relatively high salinity of its water,
(1,500 ppm. chlorides to over 4,000 ppm.) At spillway crest the reservoir
contains 3,000 acre feet and covers nearly 1,000 acres. Periodically the reservoir
affords excellent fishing for white bass and the growth rates of these fish is
unusually rapid. Much of the data included was obtained as a secondary benefit
of the study made of marine species introduced into this saline lake. However,
these data also provide information pertaining to seasonal expansions of various
populations and of the rate of increase that may occur within relatively short
periods. This reconnaissance was also to provide data on the success of stocking
from fish hatcheries and of the effect of sudden withdrawals on various species
of fish. In all 64 gill net collections captured 1,970 fish. Of these 13.85
per cent were usable game fish. The primary problematic species were longnose
gar, carp, gizzard shad and river carpsuckers. This group made up 81.37 per
cent of all fish captured. Experimental management of the reservoir may be
justifiable; however, a maximum management effort would necessarily be of
watershed scope and would depend upon management work on reservoirs located on
the Pecos above Imperial.
--- Page 28 ---
-26-
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--- Page 29 ---
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--- Page 30 ---
=38-
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--- Page 31 ---
-29-
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-30-
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--- Page 33 ---
=31=
Secondary Reconnaissance Surveys
A. Reconnaissance to Evaluate Previous Management
Lake Balmorhea is an irrigation control reservoir owned and operated by
Reeves County Irrigation District No. 1. The reservoir is 4 miles southeast
of Balmorhea in Reeves County, was constructed in 1913, and is fed by natural
springs. At spillway capacity the reservoir has 640 acres and contains 6,350
acre feet. Studies of the reservoir were initiated in June 1960. Sampling at
that time indicated that 88.78 per cent of all fish in the lake were gizzard
shad, river carpsuckers or carp. Game species were less than 8.44 per cent by
weight. More thorough reconnaissance was completed between June 13, 1961 and
October 18, 1961. Findings indicated that problematic species were 87.31 per
cent by number and 88.23 per cent by weight. On December 1, 1961, the reservoir
was treated with .20 parts per million toxaphene. Sixty days later 2,400 feet
of experimental gill nets were set and failed to capture fish. During the segment
15 experimental gill net collections were taken. As shown in the accompanying
data no problematic fish were captured. Game fish made up 100 per cent of fish
captured and growth rates were deemed adequate when the rate of stocking and
fluctuations of the lake are considered. Fishing success was meager. The fish
were not yet large enough to provide catches of acceptable sizes.
--- Page 34 ---
-32-
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--- Page 35 ---
-33-
Mountain Creek Reservoir is the primary source of municipal water for the
city of Robert Lee in Coke County. The lake has 77 acres at spillway elevation
and impounds 950 acre feet of water. The reservoir is located approximately 1
mile east of the city. Pre-management sampling of this reservoir was initiated
in May 1958 and continued through September 1960. Based upon 395 fish captured
in gill nets, it was estimated that 86.32 per cent of fish being produced were
undesirable. These fish made up 98.95 per cent of the production in weight.
River carpsuckers were 51.21 per cent of the total number of fish captured and
made up 88.66 per cent of the weight of the catch. In April 1961 this reservoir
and associated waters of the watershed were treated to eradicate existing fish
populations. On May 10, 1961, 725 feet of experimental gill nets were set in the
reservoir. No fish were captured. To evaluate the results of this management
effort, 22 experimental gill net collections were taken in the 1962-63 period.
As shown in accompanying data, bullheads were not eliminated by the treatment
or were reintroduced by March 1962. However, the primary objective, a basic
manipulation in fish production, was achieved. No carp, river carpsuckers, or
gizzard shad were captured in sampling during the twenty-two month period
following the renovation effort. Game fish exhibited excellent growth and made
up nearly 98 per cent of fish produced. Creels taken indicate that fishing
results beginning with the spring of 1962 have averaged over four fish per man
hour. There is no reason to doubt that more fish have been produced and har-
vested since the renovation effort than were captured during the previous 8 years
of the reservoirs existence.
--- Page 36 ---
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--- Page 38 ---
-36-
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--- Page 40 ---
-38-
Lake Sweetwater is one of three reservoirs owned by the city of Sweetwater
and used for municipal water supply. At spillway elevation the lake contains
11,500 acre feet of water and has 825 acres. Surveys beginning in 1957 and con-
tinuing until August 1960 indicated that 0.11 per cent of fish present were game
fish and 99.99 per cent were undesirable species. To renovate game fish production
4,256 acre feet of water contained in Lake Sweetwater and the contributing watershed
were chemically treated to eradicate existing fish. Live boxes containing 1,400
fish were suspended at various depths during the treatment. None of these fish
survived. Thirty days following the treatment 8,000 feet of gill nets were set in
the lake and captured only one channel catfish. Following the restocking program
Lake Sweetwater was closed until February 1962. At that time creel data indicated
that the average catch was 1.3 fish per man hour. This was more than 10 times as
great as was indicated in pre-treatment creels. Approximately 3,500 persons
attended the re-opening of the lake. Many of the largemouth bass exceeded 2 pounds,
and catfish were recorded as high as 3 pounds 11 ounces. Later reports indicated
that fishing success was greater later in the spring. Twenty-one gill net col-
lections taken between July and December 1961 established that bullheads, bluegill
sunfish, and white crappie had been reintroduced into the reservoir. However,
these undesirable fish made up only 10 per cent of the catch and were only 17.50
per cent of the total weight. In October of 1962, results from six gill net
collections indicated that the primary problematic species, carp, river carp-
suckers, and gizzard shad were still absent from the lake. However, bullheads
had increased to 43.66 per cent of the fish caught. These fish were being
readily taken by trotliners since they weighed over one and one-half pounds.
Largemouth bass fishing remained good during the 1962 season and excellent
catches of white crappie were reported in the early spring of 1963.
--- Page 41 ---
-39-
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--- Page 42 ---
-40-
Lake Ascarate is located in the southwest quarter of the city of El Paso
in county-owned Ascarate Park. The reservoir is supplied by wells from sub-
surface deposits, has 47 acres, and contains 247 acre feet. Survey work com-
pleted in June 1960 indicated that 93.05 per cent of the total sample weight
and 95.50 per cent of all fish present were undesirable species (Project F-5-R-8,
Job B-22). To improve game fish production for the lake, existing fish were
drastically reduced by a chemical treatment completed in August 1960. This work
was apparently successful and the lake was subsequently restocked with game fish
(Project F-14-D-4,Job 16a29). Sampling in the 1960-61 period indicated a complete
kill was achieved. Results of 6 gill nets set for reconnaissance in April 1962
revealed that black bullheads and carp had been reintroduced into the lake. The
-occurrence of carp remains unexplained; however, bullheads were introduced by
well meaning, but misinformed, sportsmen who believed them to be flathead cat-
fish. Accompanying this effort a vegetation control program was carried out to
reduce…