TPWD 1962 F-5-R-9 #780: Fisheries Reconnaissance: Job Completion Report, Texas, March 1, 1961 - February 28, 1962
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JOB COMPLETION REPORT
As required by
FEDERAL AID IN FISHERIES RESTORATION ACT
Federal Aid Project No. F-5-R-9
Fisheries Investigations and Surveys of the Waters of Region 1-B
Job No. B-32 Fisheries Reconnaissance
Project Leader Lawrence S. Campbell
H. D. Dodgen
Executive Secretary
Texas Game and Fish Commission
Austin, Texas
Marion Toole
D-J Coordinator Eugene A. Walker
Director, Program Planning
June 28, 1962
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ABSTRACT
Reconnaissance work included using nets and seines to sample fish populations
in 18 lakes and 3 stream areas. The fish obtained in 168 net sets and numerous
seine hauls were examined to determine major changes in relative abundance of
species and the size and utility of the various game fish produced. Vital factors
such as reproduction and other requirements were studied, as were basic productive
influences as water quality, aquatic vegetation and water level fluctuations.
Aspects of the fish harvest were investigated to determine public ingress and
egress, creel results, access roads and other conveniences, and the restrictions
on means and methods of taking fish. Specific reconnaissance to evaluate pre-
viously completed development work was included for three major impoundments and
several smaller bodies of water. Experiments in stocking were examined to deter-
mine initial success, and additional data on stream production were obtained to
aid in formulating better fish harvest regulations. The work accomplished during
the year is divided into five classifications that were determined by the basic
purpose or objective of the field work. These were: (1) Primary or major im-
poundment studies where up to date records 2re necessary in affording priority
to management work; (2) mew or unexplored waters investigated as a result of
requests for aid; (3) secondary reservoirs investigated for the same basic
reasons as major impoundments, but that are too small or attract too few sports-
men from too limited an area to be included under the major impoundment classi-
fication; (4) evaluation of management where waters were re-examined to deter-
mine if successful renovation has been accomplished and if the expense required
was justified; (5) acquisition of specific data to evaluate experimental
management, for providing a better basis for formulating harvest recommendations,
or where new techniques are evaluated,
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JOB COMPLETION REPORT
State of Texas
Project Ne. F-5-R-9 Name ¢ n
t B
Job No B-32 Title: Fisheries Reconnaissance
Period Govered: March 1, 1961 - February <2 1962
Objectives:
To conduct limited investigations to obtain current information concerning
gross changes in fishing conditions and factors influencing fish populations.
Techniques Used:
Gill nets and seines were used tc sample fish populations of 18 lakes and
3 streams during the year. Fish population samples were studied to determine
major changes in the balance between desirable and undesirable species and for
changes in the relative abundance, size and utility of the various game fish
being produced. Changes in the condition cf fish populations were noted and
evidence of successful reproduction and other vital fumctions were recorded. Data
regarding productive influences such as water quality, aquatic vegetation, ard
lake fluctuations were yeuouded:. Aspects affecting harvest of the resource such
as shoreline usage and access, fisherman success and the composition of creels
were also noted whe such ia Roe mation was readily aveileble or could be obtained
during the general investigetion sive effort. Inquiries and investi-
gations also included determinin sage for the watershed and possible
sources of pollution.
A total of 167 netting collections and 11 seining collections was obtained.
A netting collection is here defined as one gill net set overnight in a single
location, A seining collection is considered toe be the collective results of
seining a small area such a beach, inlet, ho bax regardless of the number
of hauls involved. Netting and seining locatio blished in previcus work
were utilized as much as was possible for s scomnaissance, Sometimes
more than one netting trip was made to the sa that sampling could be
conducted under different climatic cr seasona 1s or because the data
produced by a previous effort was obviously in et. The topography of
some lakes was such that seining was impossib eining efforts will be
reported by discussion for that reason.
major changes in the
and to ascertain changes
to determine if
2
a
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more detailed and elaborate resurvey will be required before conclusions can be
reliably determined. Some of the data are obviously insufficient and sampling
techniques are imperfect. For that reason no recommendation is made in several
instances. The equipment used included nylon gill nets, measuring 125 feet in
length, 8 feet in depth, and made up in 25 foot sections of varying size mesh.
Beginning with a l-inch square mesh section the nets increased by 1/2-inch inter-
vals in succeeding sections to a 3-inch square mesh section. Several other nets
were used for specific sampling. These had similar dimensions to experimental
nets, except their construction included 1-, 1 1/2-, 2- and 3-inch mesh sections
only. Various seines were used including a 12-foot common sense seine, and a
25- and 30-foot, one-fourth inch mesh seine,
The limited investigations conducted under recoMMaissance were primarily
motivated by a need for additional information and data to provide answers to
some of the problems outlined and discussed in Fisheries Problem Determination
reports, Job D-1, for projects F-5-R-7, F-3-R-8, and F-5-R-9. The work performed
permits the materials here presented to be organized or classified in accordance
with the basic reason or purpose for the field investigation. All waters re-
connoitered under this job are reported under a classification system similar to
that used by Bonn in reporting reconnaissance for project F-8-R-8, Job No. B-21.
More detailed reporting of specific findings for the other jobs under this project
are available in other completion reports, and the information used here is
limited to providing a general and comprehensive picture of the basic conditions
encountered. The five general classifications used are:
Glass I - Primary or Major Reservoirs Defined as lakes heavily utilized and of
primary importance to large numbers of sportsmen that travel to the
lake from a large geographical area.
Class II - New or Unexplored Waters New reservoirs, small lakes and stream
areas that have not been previously surveyed or evaluated.
Class III- Secondary Reservoirs Small lakes that are of primary importance in
a local area, but that do not commonly attract sportsmen from great
distances. Also lakes that are too small to be afforded primary
classification.
Class IV - Evaluation of Management A re-examination of waters that have been
renovated to determine if methods have been effective, and to ascertain
if the benefits obtained justify the expense required.
Class VY - Acquisition of Specific Data Experimental management efforts are
evaluated, data for formulating fish harvest regulations are obtained,
and experimental techniques in sampling are examined.
Findings:
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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lonpnose BaY---< cece ror Fees Lepisosteus osseus
gizzard shad-----3---------r rr too en Dorosoma cepedianum
banded tetra------------ errr Astyanax mexicanus
smallmouth buf£alo----------------- Ictiobus bubalus
river carpsucker---------- rrr rrr Cerpiodes carpio
gray redhorseé--------n- rrr rrr Moxostoma congestum
Carpe mcr rrr rrr err rer errr Cyprinus carpio
poldén shinér--~- -~---o-n cre Seece Notemigonus crysoleucas
spottail shiner-------------------- Notropis venustus
redhorse shiner-------------------7- -N. jutrensis
roundnose shiner--------------7----- -Dionda episcopa
plains minnoW---------errr rr cron Eybo Eybognethus placita
channel catfish---------------rr--- Ietalurus punctatus
blue catfish-------------- rr rer nnn [, f£urcatus
black bul lhead--------e---=sssee"% -I, melas
yellow bullhead-----------------2-- I, matalis
flathead catfish---~-------------- ~Pylodictus olivaris
tidewater silverside--------------- Menidia beryllina
white baSS---- rence rrr rrr errr rn -Roceus chrysops
largemouth bass----~---------------Micropterus salmoides
green sunfish----------e ner r rrr -Lepomis cyanellus
redear sunfish---------------rrrr ns -L. Microlophus
bluégill----2-- - eee eis sss Seen = -L, macrochirus
yellowbelly sunfish---------------7- dh auritus
longear sunfish-----------3err rr res . megalotis
white crapple-------r <r cree rrr ‘om, — ularis
freshwater drum------------- rere grunniens
red drum (redfish)----------------~ Sciae goal lata
atlantic croaker--------e rrr errr nn -Micropogon undulatus
spotted squeateague (speckled trout) Cynoscion nebulosus
Rio grande cichlid----------------- Gichlasoma cyanoguttatum
mosquLtofisli- -~----- ---+omsissia ss se -Gambusia sp.
Maior Reservoirs of Primary Importance
As previously stated these waters are of primary importance because of
utilization by sportsmen from extensive areas, and this utilization is regarded
as being more important than the size of the reservoir, The purpose of re-
connaissance here is to provide up-to-date information on the particular waters
productivity in game fish, and to provide a basis for affording priority to
management effort. The netting data obtained are included in tables 1 and 2.
Pertinent seining data and observations are included in the following discussion.
Hoards Creek Reservoir was constructed and is operated by the U. S. Corps
of Army Engineers. The first water impounded was in 1950. This municipal water
supply is 8.7 miles west of Coleman, has 8,640 acre feet of water at conservation
pool capacity, and at that elevation covers 510 acres. There are 11 miles of
shoreline, and the Corps of Engineers maintain excellent access roads around the
lake. Picnicking facilities and seven boat launching ramps are conducive to
heavy utilization. During the year the lake commonly ranges between 5 and 10
feet below conservation pool elevation of 1900 feet. No pollution, vegetation
or access problems were noted. The water of the lake is nearly always clear,
and pH is usually near 8.
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One of the primary changes in relative abundance of fishes as revealed by
this investigation is that the lake no longer produces or sustains a sizable
population of redear sunfish. The lake was formerly acclaimed for this asset.
One netting collection indicated the average size of these fish to be 4 ounces,
but on a second trip, when 82 of these fish were captured, the average size was
only 1.9 ounces. Another population trend, that has been expected for some time,
was the increase in gizzard shad and river carpsuckers. The capture of a single
small flathead catfish may indicate reproduction by that species has occurred.
The reservoir continues to produce excellent fishing for largemouth bass and
channel catfish, and because of its location and conveniences is highly utilized.
Seining included the capture of spottail shiners, mosquitofish, redear sunfish,
bluegill, green sunfish and largemouth bass fingerlings.
Lake Colorado City is located five miles southwest of Colorado City in
Mitchell County on Morgan Creek, At service spillway elevation this lake contains
31,800 acre feet and covers 2,030 acres. Security measures necessary to the
national defense in protecting the hydro-electric power plant on the lake's
shores continue to prevent public access to the lower one-half of the lake, This
restriction is not without public benefit as pointed out in completion report
for job B-27, Project F-5-R-7; since the restriction provides an area where
catfish reproduction is high, and where other game species can reproduce without
harassment. The lake shore area is heavily developed in private cabins, club
houses and concessions, and the areas where public access is available are limited.
In spite of these limitations the lake is heavily fished by sportsmen that travel
from distances of over 200 miles.
Netting and seining collections reflect the tremendous production of game
fish by this reservoir. Over 60 per cent of netting collections consisted of
channel catfish, largemouth bass and desirable white crappie (avg. wt. 8.9
ounces). Another prime fishery that is not particularly apparent in examination
of netting data is the flathead catfish population, These fish are much sought
after and are often captured by local anglers. Although gizzard shad and river
carpsuckers are established in this lake they do not yet appear to be as detri-
mental to game fish production as is apparent in other regional waters. Large-
mouth bass appear to be increasing through natural spawning success and because
of other factors that are not clearly understood. This is unusual for the region
and the apparent failure of white bass to increase after being introduced is not
consistent with trends common to the region. The effect of phenomena unique to
this lake will require further study. Seining captured gizzard shad, spottail
shiners, redhorse shiners, largemouth bass, bluegill and white crappie.
Lake Nasworthy is the primary source of municipal water for San Angelo,
Texas. This lake is 6.5 miles southwest of the city and impounds the middle
and south Concho Rivers. At spillway capacity 1,300 acres are covered, and
volume at that elevation is about 12,390 acre feet. Bulrushes (Scirpus),
cattails (Iyphus) and yellow water lillies (Numphar) continue to offer some
obstructions to fishing and boating. However, as a result of chemical control
measures described and reported in completion report for Job. No. 15a7, Pro-
ject F-15-D-3, the shore areas are open to fishing, and in many instances the
vegetation provides some protection from harassment by skiers. It is possible
that the increase in largemouth bass may also be attributable to the clearing
of shore areas, This work not only provided a greater spawning area and reduced
harassment, but also permits circulation of the waters immediately adjacent to
the shores and reduces excessive temperatures and stagnation, Public utilization
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and interest in this lake remains intensive and the construction of facilities
to permit and encourage recreation continues. Many sizable catches of largemouth
bass and flathead catfish have been observed during reconnaissance, and there is
little basis for doubting that the game fish produced and harvested is greater
than has occurred for many years.
Only five gill net collections were made and these data do not indicate
significant changes in relative abundance. The lake's fish populations appear
to have reached a static balance, with gizzard shad and river carpsucker main-
taining their dominance. The failure to capture white crappie is regarded as
a sampling deficiency.
The potential development of a desirable fishery resource on the south and
middle Concho watersheds and a subsequent renovation of Lake Nasworthy is dis-
cussed in the resurvey report for Project F-5-R-8. The dam that will create
the reservoir above Lake Nasworthy is scheduled for completion in October of
1962, The addition of a hydro-electric power plant to the shores of Lake Nas-
worthy may be a means of improving and sustaining the game fishery resource.
Oak Creek Reservoir is 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. Practically no run-off has entered the
lake for over a year and the lake level was down nearly 13 feet when the col-
lection was made in January of 1962. The current volume of 16,456 acre feet is
the least quantity of water contained since the reservoir filled in 1953.
Associated with this recession, extended periods of turbidity have occurred
and food production was adversely affected. There has been a noticeable de-
cline in the quantity of the game fish harvest and few desirable creels have
been reported during the year.
Table 5 provides the results of 10 netting collections obtained. The
dominance by river carpsuckers as indicated by the netting sample is considered
near typical of collections obtained under the circumstances. However, the
indicated increase in relative abundance of those fish (from 13.99 per cent in
1960 to 80.95 per cent in 1962) is considered highly significant. This increase
supports the previous prediction that conditions of low water would result in
an acceleration of the trend of undesirable fish toward complete dominance.
There may also have been a corresponding increase in flathead catfish as was
reported by responsible sportsmen. Further reconnaissance should be conducted
at this lake to ascertain trends of populations, and if further recession occurs,
to provide more extensive background data to decide what management effort is
most likely to be fruitful. A study of the effect of the newly created power
plant upon fish populations might also be justifiable.
San Angelo Reservoir is a primary flood control structure constructed
and operated under the auspices of the U. S. Corps of Engineers. The dam is
adjacent to the northwestern residential section of San Angelo, and at con-
servation pool the reservoir contains 119,188 acre feet of water. The water
impounded is a secondary source for municipal water, and at conservation pool
elevation approximately 5,456 acres are covered. For the third consecutive
year the lake was receded by over 30,000 acre feet below conservation storage.
As previously pointed out, the unobstructed expanse of open water is detri-
mental to fishing because of the frequency of occurrence of prevailing winds.
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However, heavy public fishing continues. On week ends and holidays launching
areas and other facilities are always crowded. White bass, largemouth bass, channel
catfish and small white crappie sustain fishing.
Results of netting collections are in tables 6 and 7. Fish populations may
have reached a near static condition, and the average size for most game fish
taken is large. This has motivated a decision to hold the state plug fishing
contest on this lake, and it is expected that the results from this fishing, by
highly skilled anglers, will be high and should exceed results from some lakes
previously selected. However, the apparent lack of natural reproduction by
largemouth bass indicates that those fish are declining numerically. One interest-
ing aspect of netting done near the entrance of the river was the capture of 46
freshwater drum. Although seven of these fish were netted in resurvey work for
Project F-5-R-7, none were taken in previous sampling. These fish are normally
difficult to capture in routine netting with the equipment normally used. It
may be possible that San Angelo reservoir has sustained a higher population of
drum than indicated; since these fish appear to concentrate in specific locations
and their chance capture in samples might not have occurred. However, it is
believed more probable that substantial quantities of these fish have entered
the lake by migrating from the watershed above. Reconnaissance should be con-
tinued with the view that renovation of this reservoir should be accomplished
when the other area waters are providing desirable game fish production in
order that a rotation type management plan can be put into effect. Seining
indicated reproduction by gizzard shad, carp, and white crappie. Spottail
shiners and redhorse shiners were also captured by that method.
New or Unexplored Waters
The following data and discussion pertain to waters that had not been
previously investigated. The motivation for including this work under recon-
naissance is varied. In several instances the work was done at the request of
municipal authorities while other work was in progress on nearby waters of
primary or major importance. Other minor reservoirs were the only public
fishing waters for a particular locality where past utilization indicated
management would be justified. Investigations of unknown waters were also made
when a basic rotation management plan was being considered for a particular area.
In these situations the secondary reservoir would serve to provide limited
fishing while renovation procedures were being employed to improve production
in a primary or major reservoir.
Santa Fe Lake is privately owned by the Santa Fe Railroad, and is located
3 miles north of Sweetwater in Nolan County. The lake covers about 80 acres
at spillway elevationand was near capacity at time of survey. This is an old
lake constructed about 1926 and is greatly filled in by siltation. The lake
is primarily fished by anglers for sunfish,and public fishing is limited.
Shore fishing predominates methods used and access roads around the lake are
needed, Vegetation is a primary problem as much of the shore is congested
by pondweeds (Potamogeton), and muskgrass (Chara).
Netting results from this investigation are shown in table 8. Largemouth
bass were not captured in this netting, but fingerling bass were secured in
seining and larger fish are known to be occasionally taken by sportsmen. The
average size for sunfish and crappie is interpreted as being indicative of
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stunting through excessive numbers of those species, and channel catfish appear
to be the most significant fishery resource.
There is little doubt that this lake is not fished intensively enough by a
sufficient number of persons to justify spending any sizable amount of federal aid
money. However, the lake has served as an alternate source for fishing while
renovation of Lake Sweetwater was being effectuated, and can be expected to supply
similar aid if Lake Trammel or Oak Creek Reservoir are included in future develop-
ment work, Members of the board that control and regulate the lake have indicated
that they may be interested in spending part of the revenue taken by sale of boat-
ing permits to control the aquatic vegetation or to improve the game fish pro-
duction. It is recommended that management and further investigations of this lake
be turned over to the state biologist for inclusion in that category of the
regional work.
Secondary Reservoirs
The waters included under this category are usually of primary importance
only in relatively small and localized areas. Some of the waters are simply too
small to be afforded primary classification; although the yield in game fish on
a per acre basis may exceed many primary waters. A few of the waters here de-
signated as secondary reservoirs may be elevated to major classification in the
future, when utilization and productivity warrant the change.
Novice Lake is a former water supply for that city and is located on Jim Ned
Creek watershed about 30 miles west of Coleman in Coleman County. The lake has
about 40 acres and volume is not known. The lake has afforded excellent fishing
in the past and the reconnaissance work was completed at the request of local
sportsmen who desired recommendations to restore fishing.
As shown in Table 9, gizzard shad and carpsuckers dominate the lake. Stunted
crappie are excessive and bullheads further complicate and detract from game fish
production. Renovation is recommended when federal aid requirements are met.
Old Winters Lake is a former water supply for the city of Winters in northern
Runnels County on Elm Creek watershed. The lake has about 50 surface acres and
impounds about 250 acre feet when at spillway level. In compliance with requests
from the municipal authorities, reconnaissance work by seining was completed in
the spring of 1961. The lake had receded at this time to less than 30 acre feet
of water and was completely dominated by carp and gizzard shad. Following this
investigation the lake was eradicated and subsequent restocking is expected to
effectuate complete renovation.
New Winters Lake. Reconnaissance sampling of this 250 acre lake was completed
during the spring of 1961. This reservoir was much receded from its spillway
capacity of about 11,000 acre feet at the time, and turbidity was high as a
result of suspended red colloidal materials. As shown in Table 10, gizzard shad
and river carpsuckers dominated fish population. However, significant channel
catfish and white crappie populations apparently afford some successful game
fish production. The data obtained are entirely insufficient, and further
reconnaissance: will be necessary in the future.
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New Anson Lake is located 9 miles north of Anson and is that city's primary
water supply. The lake was maintained near spillway capacity during the year and
at that elevation covers about 350 surface acres. Suspended colloidal materials
provide turbidity and help to control submerged aquatic vegetation, but yellow
water lillies (Numphar sp.) render fishing in the shallow shore areas difficult.
Netting data in Table 11 indicate that gizzard shad, river carpsuckers and
black bullheads dominate rough fish species. Channel catfish and small white
crappie constitute the bulk of game fish captured, Seining was unproductive due
to the previously mentioned vegetation; however, many small sunfish and minnows
were observed,
There are no shore access roads around this lake and only one launching
area is accessible. A significant portion of the lake is surrounded by private
property, and this area is fenced to prohibit access to fishermen, It is
believed that if a road could be opened up over the dam the lake would be more
accessible and would as a consequence accommodate more fishermen,
Qld Anson Lake is a former water supply for Anson and is approximately 4
miles south of that city. It was estimated that the lake usually covered about
80 acres during the project period. Much of the shoreline is inaccessible to
sportsmen, access being prohibited by bulrushes (Scirpus). The city purchased
the chemical required for control of these plants and limited application has
been initiated.
Results of netting collections are in Table 12 and Table 13. The only
significant aspect of the limited data obtained is the abundance of golden
shiners that were captured in the March netting. Since only 25 feet of each
experimental gill net used was capable of capturing these fish, it is con-
sidered likely that a large population of these shiners is present. The second
netting was made primarily to explore this problem and only six individuals
were captured. Golden shiners and bluegills that were rather small appear to
be the only undesirable species presently occurring in the lake in great numbers,
Seining was again unproductive because of the limited area where sampling could
be accomplished.
Lake Trammel is located 5 miles south of Sweetwater, and is one of three
sources of municipal water. This lake is the control reservoir into which water
is pumped from Oak Creek Reservoir, At spiliway elevation the lake covers about
200 acres and contains 2,500 acre feet. Water in the lake is normally clear but
the water usage practices result in extreme fluctuation, Boat launching
facilities and access roads around the lake are very limited, and occasionally
aquatic vegetation reduces the effectiveness of fishing for the lake shores,
Many anglers that fish at Lake Trammel are "bream" fishermen, and it would be
desirable if more shoreline access roads were available,
Table 14 indicates that fish populations in this lake are primarly game
species, These data are in accord with initial survey findings and with data
from resurvey completed under Projects F-5-R-6.and F-5-R-7; Although the average size
of white crappie captured in collections was only 2.3 ounces, several of the
individuals netted were of desirable size. Channel catfish were not captured
in reconnaissance netting, but previous investigation has established that a
sizeable and healthy population of these fish exist. Extreme changes in relative
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abundance apparently have not occurred since 1960. Management work for this
reservoir is not deemed of primary importance until after a satisfactory re-
novation of Oak Creek reservoir is possible. Restocking may not be needed
as largemouth bass juveniles, green sunfish, redear sunfish, bluegills, orange-
spotted sunfish, white crappie, and bullheads were captured in seining.
Lake Balmorhea is 4 miles southeast of Balmorhea in Reeves County. The
reservoir is heavily utilized for fishing, and extensively developed for re-
creation. The 640 surface acre, 6,350-acre foot reservoir is owned and operated
under the duspices of Reeves County Irrigation District No. 1, and has provided
excellent fishing in the past. In addition to run-off from the watersheds that
contribute to Madera and Toyah Creeks, the lake is sustained by the permanent
flow from San Solomon, Giffin, Phantom, and Saragosa Springs. The combined
flow from these springs exceeds 90 acre feet of water per day.
Tables 15 and 16 show the results from reconnaissance netting, and these
data are the basis upon which a decision to eradicate existing fish life is
sustained. The reservoir and Toyah Creek, as well as connecting canals, was
treated between December 1, 1961, and January 28, 1962. For complete details
pertaining to the lake and its renovation see completion report for Job 16a34,
Project F-14-D-6. It is recommended that reconnaissance in the 1962-63 period
include extensive procedures to evaluate the benefits obtained from this
management.
Lake Balmorhea is placed under this category solely because it had not
been previously surveyed, and will in all probability be re-classified to be
included under the primary or major impoundment category within the existing
segment,
Lake Scarborough is located 8 miles north of Coleman. This lake covers
111.3 acres and contains 1,638.2 acre feet of water when at spillway capacity.
The lake was at this level during most of the segment. Since reconnaissance
netting data indicated a large population of gizzard shad, and because it was
also known that freshwater drum were abundant in the lake, it was decided that
a selective kill technique should be employed to reduce the problematic species
of fish. The rigid schedule of federal aid personnel prevented their including
this job during the fall of 1961. The work was completed by the state biological
crew and per diem and other travel expense was paid by the state without federal
aid. It is estimated that approximately 90 per cent of the shad population was
destroyed, and no drum were netted by the state crew after the treatment. The
details of this job are reported on a separate report entitled: "Selective
Kill of Undesirable Fish at Lake Scarborough". The evaluation of results of
this work will be included in reconnaissance for the coming year.
Evaluation of Management
All of the waters discussed under this sub-heading have been renovated by
eradicating existing fish and restocking with hatchery reared game fish. Usually
these evaluations were completed at opportune times when field work for re-
conngissance or survey work was being carried out on nearby waters or when it
was necessary to decide when the lake should be reopened to fishing.
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Champion Creek Reservoir is the sister lake to Lake Colorado City and was
renovated in 1959. This reservoir is located approximately 8 miles southeast of
Colorado City in Mitchell County. The lake is capable of impounding over 41,000
acre feet of water. However, at no time since the impoundment was completed in 1958
has water volume exceeded 13,000 acre feet. During the project period volume con-
tained never exceeded 10,000 acre feet. Fishing success has been excellent and
progeny from successful reproduction by largemouth bass and other game species were
observed in abundance. Netting results from two trips made during the segment do not
indicate significant changes in fish populations when compared with previous data.
However, the dormant problem represented by the existence of golden shiners, black
bullheads and green sunfish may increase at any time. Channel catfish captured
appeared to be some of the fish released from hatcheries because of the uniformity
of their size. There have been reports of successful reproduction by the 22
flathead catfish moved to this lake from Lake Colorado City; however this is not
confirmed.
The access problem was acute for over a year because of the failure of the
city of Colorado City and the Texas Electric Service Company to reach an agreement
and ratify a contract that would satisfactorily designate liability. This problem
is somewhat alleviated by recent ratification of such a contract; however, access
roads are generally in poor condition and remain a problem. A large area of the
lower portion of the lake is restricted and is patrolled by employees of the Texas
Electric Service Company to exclude public access. The area involved is less than
at Lake Colorado City. A sizeable increase in volume would greatly expand the
reservoir beyond the old stream banks and is regarded as all that is presently
needed to establish a productive fishery that could last for several years.
Mountain Creek Reservoir is 2 miles east of Robert. Lee in Coke County,
and is that city's municipal water supply. At spillway elevation the reservoir
impounds 950 acre feet and covers 77 acres. A fish eradication for this lake and
parts of the contributing watershed was completed in April 1961. Complete details
of that work are reported in the completion report for Job 16a32, Project F-14-D-5.
Table 20 shows the results of five net collections in Febuuary of 1962,
10 months after the eradication treatment and subsequent restocking. A total kill
was believed to have been achieved and the occurrence of green sunfish, golden
shiners and bullheads is attributed to fish being washed down from the watershed
above or to some other means of inadvertent reintroduction.
It is recommended that intensive reconnaissance be made during the spring
of 1962 in order to provide a basis for recommending an opening date for resuming
fishing, Seining also indicated the presence of redhorse shiners, mosquitofish
and green sunfish.
Lake Sweetwater was chemically treated on August 27, 1960, as part of a
watershed renovation program, At that time 4,256 acre feet of water was impounded
and covered 366.19 acres. The lake has contained near this same volume with
slight variations of the water level since that work was completed. At spillway
capacity the lake contains 11,500 acre feet and covers approximately 640 acres.
Lake Sweetwater is now a secondary source for municipal water and is located 9
miles south of that city. The details of the fish eradication and restocking are
given in completion reports for Job No. 16a23, Project No. F-14-D-4 and Job No.
18all, Project No. F-14-D-5.
--- Page 13 ---
=I1=
Since renovation the water has remained extremely clear, and as a result,
vegetation predominated by Algae and Chara have expanded in some areas. There
are also a few scattered patches of smartweed (Polygonum)around the lake's
shore resulting in an abundance of food for game fish being produced. Seining
résults indicate successful reproduction by largemouth bass, redhorse shiners
and spottail shiners.
The results of 21 netting collections are given in Tables 21 and 22. It
is evident that sunfish and crappie have been reintroduced. This is believed to
have occurred through a misunderstanding of stocking instructions and possibly
through sportsmen releasing some of these fish in a misguided desire to help
improve the lake.
lake Sweetwater was reopened to public fishing on February 15, 1962, 18
months following the date of treatment. Creel census conducted on that day
indicated the average catch in fish was 1.3 fish per man-hour. This is more
than 10 times as great as indicated in creels examined prior to renovation.
Approximately 3,500 persons attended the opening. Many of the largemouth bass
captured exceeded 2 pounds, and catfish were recorded as high as 3 pounds 11
ounces, It is believed that warmer weather will increase both fishing pressure
and yield.
Acquisition of Specific Data Needed
This final category could be regarded as a catchall for reporting
miscellaneous reconnaissance data, Included here are results of all minor
sampling that was done with very specific and limited objectives in view. For
instance, this year sampling at Imperial and Red Bluff Reservoirs was primarily
to attempt recapture of marine fish experimentally introduced, and the re-
connaissance data obtained in that work are biased as a result. If sampling
had been primarily motivated by a desire for knowledge of relative abundance,
then both of these reservoirs would have been included under major reservoir
classification. The sampling of the lower Pecos River and the Colorado River
near Robert Lee was done to provide information pertinent to the production of
bait species so that aspects of the reproductive requirements for those fish
might be revealed and better understood. These studies will be continued from
time to time, and are expected to provide a better basis for formulating future
harvest regulations by supplying a better idea of how many and what kind of fish
can be harvested without detrimental effect on the basic resource. It is
possible that over a period of years many aspects of the life histories of many
species may be worked out in this manner, and the knowledge gained could provide
a basis for improving management through a better use of the naturally produced
forage. Such studies could also provide the means of diversifying and improving
hatchery production, and might provide information that would benefit the over-
all program. Inquiries were also made to determine if stocking experiments
using largemouth bass fry were successful.
Red Bluff Reservoir is located on the Texas-New Mexico line about 60 miles
north of the city of Pecos in Reeves County. The dam impounds the Pecos River
and was constructed primarily for irrigation. For that reason fluctuations are
often as great as 30 feet within a 10-month period. Because of these fluctua-
tions natural reproduction of largemouth bass rarely occurred. It was believed
that by taking advantage of the growing room created by the annual increase in
volume that normally occurs during the winter when withdrawals are minimized,
a substantial improvement in largemouth bass production might be effectuated
by stocking with large quantities of bass fry during the early spring. This
--- Page 14 ---
-12-
was done in the spring of 1960 and all evidence indicates at least temporary
success. Reports of fair largemouth bass fishing in the fall of 1961 were
believed to be reliable, and the ‘yearling! size and uniformity of the fish
captured indicated that the fish were from the same age group. Other results
are in Table 24. The successful recapture of marine fish introduced is reported
in detail in completion report for Job No. F-1, Project F-5-R-9.
Imperial Reservoir is a control reservoir for Red Bluff Power and Water
District and is located in a bend of the Pecos River near Imperial in Reeves
County. The reservoir continues to afford excellent white bass fishing and
other results are as shown in Table 23. The reservoir is heavily utilized
and access roads are being improved, The limited area of the lake, about
1,000 acres, often results in harassment and competition between fishermen
and other recreationalists.
The Lower Pecos River was sampled by seining and netting near Imperial
and by seining at the mouth of Howard Draw near Pandale. Netting in the Imperial
aréa was an unsuccessful attempt to secure or recapture marine fish introduced
in 1957. However, data obtained indicated that the stream was dominated by un-
usually large gizzard shad and other species of questionable utility. This may
have been the results of selective sampling because dense submerged vegetation
prevented gill nets from being placed on the stream bed.
The production of minnows near the mouth of Howard Draw was tremendous
and seining indicated spawning by the principal species of that area may be
almost entirely dependent upon stream flow. Inquiries pertaining to the success
of stocking of largemouth bass fry mear the mouth of the river indicated that
a relatively stable population of those fish have been created. However, as
pointed out in completion report for Job B-15, Project F-5-R-8, many centrarchid
populations are damaged by periodic floods that reduce dissolved oxygen below
critical requirements. The benefit achieved is at best temporary.
The Upper Colorado River near Robert Lee was seined to provide data on
the various minnows present. Data obtained indicated that late fall or even
winter spawning may occur and that spring production is usually higher when
flow is sustained during the winter.
Recommendations:
It is recommended that this job be continued, and that future efforts
include additional efforts to determine more specifically what is required to
maintain stream productivity.
Prepared by Lawrence S. Campbell Approved by
Project Leader Coordinator
Leo D. Lewis
Regional Supervisor
Date June 28, 1962
--- Page 15 ---
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