TPWD 1959 F-5-R-6 #489: Inventory of Species Present in Lake Trammell near Sweetwater, Texas: Job Completion Report, Dingell-Johnson Project F-5-R-6, Job B-2h
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Report of Fisheries Investigations
Inventory of Species Present in Lake Trammell near
Sweetwater, Texas.
by
James F. Wilcox
Assistant Project Leader
Dingell-Johnson Project F-5-R-6, Job B-2h
April 16, 1958 — April 15, 1959
H. D. Dodgen - Executive Secretary
Texas Game and Fish Commission
Austin, Texas
Marion Toole Kenneth C. Jurgens & William H. Brown
Coordinator Assistant Coordinators
Job Completion Report
State of TEXAS
Project No. FwSmRmé Name: Fisheries Investigations and Surveys of
the Waters of Region 3—B.
Job No. B~2h Title: Inventory of Species Present in Lake
Trammell near Sweetwater, Texas.
Period Covered: April 162 1958 w April 15, l9§9
Abstract:
The results of the netting and seining samples indicate that channel catfish
(Ictalurus punctatus) and bluegill sunfish (Lepomis macrochirus) are the most abundant
game species in Lake Trammell and that the abundance of black bullheads (Ictalurus males)
is the principal "rough fish" problem. It was also concluded that most of the members
of the family Centrarchidae (black basses and sunfishes) occurring in the lake are over-
populated and therefore stunted. The only recommendation made was to introduce yellow
catfish (Pylodictus olivaris).
ijectives:
To determine the species present and their relative abundance as well as to determine
the ecological factors influencing their distribution.
Procedure:
Six netting stations were established on Lake Trammell. Each station, with the ex-
ception of station one, was netted three times. Station one was netted twice in June
but could not be used in August because the water level was lower than in June and the
station was too shallow. A total of seventeen netting collections were obtained. All
nets used were experimental type nylon gill nets, measuring 125 feet long by eight feet
deep and made up in five, 25 foot sections. Mesh sizes for these nets increased pro-
gressively in each following section, at halfeinch intervals, beginning with a one-inch
square mesh section and terminating with a threeminch square mesh section. Locations
of the netting stations used are shown on Map No. 1.
All fish caught in the gill nets were weighed, measured, and their sex and condition
determined. Some species were checked for stomach contents and parasites.
Only two seining stations were established due to factors discussed elsewhere in
this report. Several seining drags were made at each station during both the June and
August trips to Lake Trammell and the composite of these drags at each station for each
trip was counted as one seining collection. A total of four seining collections were
obtained. The seines used were 20 feet long by four feet deep, with % inch mesh.
All fish caught in seines were preserved in a 10% formalin solution and taken to
the laboratory for identification.
A water sample was taken and analyzed. The results of these analyses are presented
in Table VI. Surface temperature, pH, and turbidity were measured and recorded for each
trip. Notations concerning the description and general ecological conditions of the
lake and surrounding terrain were recorded. Further ecological and hydrological in—
formation was obtained from the City of Sweetwater.
Findings:
Physical Characteristics w Lake Trammell is located on Sweetwater Creek approximately
seven miles southwest of the City of Sweetwater and is a part of the Brazos River System.
The contributing watershed above the Lake Trammell Dam drains an area of SA square miles
(Map No. 2). The dam was constructed in l9lh as a water supply for the City of Sweetwater.
When built the lake could contain 3,183 acre feet of water or 1,039,952,812 gallons at
maximum capacity. The maximum capacity of this lake is probably not as great today, due
to siltation which has occurred during the last fortwaive years. When full Lake Trammell
covers approximately 230 surface acres.
Excess water pumped from Oak Creek Reservoir near Blackwell, Texas, is stored in
Lake Trammell. Oak Creek Reservoir is, incidentally, the chief source of water for the
City of Sweetwater. Another source of water is Lake Sweetwater which is located approxi—
mately nine miles east of Lake Trammell.
The recorded pH for Lake Trammell is 7.6. The water temperatures ranged between
32 degrees Fahrenheit and 8h degrees Fahrenheit. The water is relatively clear most of
the time with a measured light penetration of 6 feet (Secchi).
The area surrounding Lake Trammell is composed of rolling uplands, with broad level
valleys and plateaus and is interspersed with prairies and mesquite and cedar woodlands.
The soil is chiefly dark red loams and stony soils of limestone origin. There appears
to be only a small portion of the Lake Trammell watershed in cultivation.
Most cover is mesquitewgrassland and cedar-grassland association, with button willows
and desert willows abundant along the creek bed. °
Aquatic Vs station n The principle types of vegetation in and around the lake shore
are smartweed {Polygonum.§p.), mud plantain (Heteranthera‘sp.) (prdbably Heteranthera
dubia), pondweed (Potomogeton sp,), stonewort (Chara sp.5, and coontail (Ceratophyllum
£235. Various types of algae occur as "blooms" and filamentous sheets.
Copper sulfate is applied to the lake by the City of Sweetwater nearly every summer
as a means of vegetation control. This treatment has only a temporary effect apparently
since the lake characteristically contains profuse aquatic vegetation.
Pollution m There are a number of pumping oil wells on the lake shore and in the
lake's watershed. At the present time no petroleum or saltwater pollution can be de-
tected in the lake and it is believed that none exists. Other pollutants such as cotton
insecticides and organic debris which might wash into the lake in times of heavy rains
do not appear to have ever been concentrated enough to cause serious fish kills. This
is probably due to the limited watershed and the small amount of land in cultivation on
the drainage area. Some minor fish kills have been reported by local observers. These
can possibly be attributed to natural oxygen depletion occurring when the plankton bloom
is heavy and when several cloudy, still days occur. No oxygen depletions were noted dur-
ing the course of the survey.
Recent History a Lake Trammell went dry in the summer of 1953 due to the severe
and prolonged drouth but was filled by spring rains in l95h and restocked by the state
fish hatchery. The lake was closed to fishing until April of 1956. When first opened
in 1956, bass fishing was good but at present bass are rather hard to catch. Small
sunfish and crappie are fished for rather heavily by local anglers, with a high degree
of success. Trotlines are allowed in the lake but are not employed too frequently. Many
bullhead catfish are caught from the shore.
Netting _ Tables I, II and III give the statistical data obtained from the netting
collections. A total of 3A2 netted specimens were collected. Of these, 210 were game
species and 132 were rough and/or forage species.
Only 16 fish were collected per 100 linear feet of net. Two factors probably account
for this sparseness of specimens. One is the fact that the water in the lake was very
clear during the times netting collections were being made (6 feet Secchi). The other is
the fact that many of the fish in Lake Trammell are apparently stunted and only a small
portion of each of the experimental nets used had small enough mesh to catch such small
fish.
Descriptions 9f Netting Stations
Station No. 1 m The water was approximately 8 feet deep on June hth and 5th, 1958,
and only about 3 feet deep on August 20th. This station was not netted on August 20th
because of the shallowness of the water. This station is over the creek channel but the
channel is badly silted and sanded in. There are partially inundated willow trees along
the edge of this channel which the nets were tied to. Across the channel from these
willows is a sandy shore covered with smartweed. These plants were blooming during the
June trip.
Station No. 2 m The water was approximately 12 feet deep at this station during the
June netting and only about 7 feet deep during the August netting. This station is very
similar to station No. 1 since it lies about 75 yards down the creek bed from it and is
bordered by willow trees on one edge of the channel and a sandy shore covered with profuse
growths of smartweed on the other.
Station No. 3 _ The water was approximately 12 feet deep at this station during
the June netting and about 7 feet deep during the August netting. This station is at
the mouth of a small slough. The net was tied to a large willow tree at one end and
the other end was stretched towards the slightly sloping shore which was covered with
mud plantain and smartweed. 'The bottom was soft mud and silt covered in the shallows
with various types of submerged aquatic vegetation.
Station No. A m The water was approximately 1% feet deep at this station during
the June netting and about 9 feet deep during the August netting. This station is in
open water except for four large posts emerging from the water in a rectangular pattern
about 10 feet apart. One end of the net was tied to one of these posts and the other
end was stretched towards the west shore.
Station No. 5 a The water was approximately 15 feet deep at this station during the
June netting and about 10 feet deep during the August netting. One end of the net was
tied to a large rock emerging from the water near the bank. The bank consists of a
rapidly declining gravel and clay bottom at the base of a sheer red clay cliff. The
other end of the net was in open water.
Station No. 6 m The water was approximately 13 feet deep at this station during
the June netting and about 8 feet deep during the August netting. One end of the net
was tied to a large rock lying among some larger sandstone rocks on an erratically de-
clining bank. The other end of the net was in open water.
Seining - The use of seining as a sampling method for inventory of fish species
was very limited in Lake Trammell. Factors which hindered the catching of fish by
means of seines include: 1. the extreme slope of much of the shoreline; 2. the thick
mats of both emerged and submerged vegetation in areas of shallow water; and 3. the
relative clearness of the water.
Only two areas were productive enough to be considered as seining stations. Attempts
to sample the fish population by seining were made in several other areas besides those
listed as seining stations, but with little or no results due to the aforementioned
"natural" conditions of the lake. Due to the inadequate seining sample there are prObably
several small species of fish in the lake which were not collected at all.
Table IV gives the statistical data Obtained from the seining sample.
Descriptions 9f Seining Stations
Station No. 1 w The water ranged from approximately A feet in depth out about 15
feet from the water's edge to about 1 inch in depth at the shoreline. The bottom was
fairly firm being composed of sand, gravel and rubble. There were a few scattered plants
of smartweed but not enough to seriously interfere with seining activities. This station
is also the lake's boat launching area. '
Station No. 2 m The water ranged from approximately A fast in depth out about 10
feet from the shoreline to about 1 inch in depth at the shoreline. The bottom was sand
and silt covered with various forms of aquatic vegetation. This vegetation impeded
seining to a certain extent. This station was along the shoreline in a small slough.
Discussion gfaFisherl Population w The pertinent information obtained concerning
the fishery population in Lake Trammell can best be discussed by means of the following
annotated checklist of species.
Annotated Species List
Cyprinidae1§8hiners and minnows)
Notemigonus crgsoleucas {golden shiner) a Collected by netting only, this species
has apparently outgrown its utility. The individuals Obtained in the netting sample
were so large that only a large largemouth bass could forage on them. Some observers
believe this species is destructive to largemouth bass spawning nests. For these reasons
it is concluded that this species as it appears in Lake Trammell is fairly undesirable.
Notropis lutrensis (redhoree Shiner} e Only three individuals of this species were
collected by seining. It is believed that this species is much more prevalent than
this sample would indicate since a number of shiners were observed in the lake that could
not be successfully seined. This species is considered to be desirable since its size
never becomes large enough to prevent it from being consumed by other fish.
Ameiuridgg (Freshwater catfishes)
Ictalurus punctatus (channel catfish) — Sixty—five individuals were collected
by netting which indicates that this species is the most abundant large game fish in
the lake. These fish composed over 19 percent of the netting sample by number and over
7h percent by weight, with an average weight of 2 pounds and 2 ounces. Not many cat—
fish are taken from the lake by anglers according to the lake keeper although trotlines
are allowed in the lake. The probable reasons for this condition are that not many
trotlines are set and there is an abundance of small fish in the lake which provide many
natural baits for the catfish, and also a large amount of aquatic vegetation which they
utilize for food. Most specimens collected had visceral roundworms.
Ictalurus melas (black bullhead) - Collected both by netting and seining, these fish
appear to be the most abundant species in the lake. The netting sample contained 107
specimens of this species which composed over 31 percent by number. They are fished for
by a segment of the anglers but, in general, are considered to be highly undesirable.
Lake Trammell contains no yellow catfish which apparently serve as a partial control on
the bullhead population in other West—Texas lakes.
Poeciliidae (Mosquitofishes)
Gambusia affinis (common mosquitofish) — Gambusia composed only 10 percent of the
seining sample but are known to be extremely common since schools of these fish were
observed on the surface of the water in many areas. This species does not appear to be
a preferred food of other fish but is sometimes consumed in the absence of other more
desirable forage fish.
Centrarchidae (Black basses and sunfishes)
Micropterus salmoides (largemouth bass) - This species was collected by both netting
and seining. Lake Trammell appears to have a large supply of small largemouth bass but
no large ones were Obtained in fish collections and not many large ones are reported
caught by anglers. The natural reproduction of this species appears to be great in this
lake and the state fish hatchery also stocks this species in the lake nearly every year.
Most specimens obtained ranged in total length between 55 and l65nflllimeters. The data
collected and observations made of these fish somewhat indicate that many of the individ-
uals of this species are slightly stunted.
Lepomis cyanellus (green sunfish) _ This species was collected by seining only. Most
individuals taken from Lake Trammell were very small. Probably due to the large size of
their mouths, these fish seem to compete directly with the small base for small minnows
and similar forage.
Lepomis microlophus (redear sunfish) w Redear were collected by seining only. There
were some very large individuals of this species observed in the clear waters of Lake
Trammell. These fish are apparently subdominant to other species of sunfish but possibly
due to different feeding habits attain a much larger size.
Lepomis macrochirus (bluegill sunfish) - Bluegills collected both by netting and
seining composed over 17 percent of the netting sample and over 50 percent of the sein-
ing sample. This species is prObably the most numerous game species in the lake and also
appears to be an important forage fish for other species. This species is overwpopulated
in lake Trammell and does not reach a large enough size to be considered a highly de—
sirable game fish. However, there are a great number of sunfish fishermen who take large
strings of the stunted sunfish from the lake.
Pomoxis annularis (white crappie) m Collected only in netting, these fish composed
over 25 percent of the sample. This is another species that appears to be overwpopulated
and consequently stunted. Individual crappie averaged only 2 ounces in weight.
Percidae (perches and darters)
Porcine caprodes (logperch) m Though collected sparcely in seining, are probably
more abundant than the sample would indicate. This statement is made because this species
is usually on the bottom of the lake or around obstructions and normally cannot be seined
in significant numbers. They are considered to be relatively unimportant to the ecology
of the lake.
Conclusions and Recommendations:
All the desirable species of fish in Lake Trammell with the exception of redear
sunfish and channel catfish appear to be overepopulated, and as a result, stunted. One
reason advanced for this condition, besides the fact that members of the family Centrarchidae
are naturally very prolific in most Westhexas waters, is that the profuse beds of aquatic
vegetation in Lake Trammell afford too much cover for the small fish and therefore their
numbers are not reduced enough by larger fish to prevent over-population.
The only really undesirable species found in the lake were black bullheads and golden
shiners. It cannot be concluded then, at this time, that the lake‘s fishery population
is enough out of balance or that the rough fish numbers are great enough to recommend a
complete eradication of fish species. However, since the water from Lake Trammell can be
pumped out rather quickly and used for the City of Sweetwater's water supply and then the
lake can be refilled from Oak Creek Reservoir. it might be feasible at some future date
to substantially reduce the amount of water as described and perform a complete eradication
on the remaining pools. This procedure could be done only when the condition of the fish-
ery population warrants it and then only with the full cooperation of the City of Sweetwater.
It is then concluded that the only immediate recommendation that can be made is that
yellow catfish Egylodictus oliveria) be introduced in the lake when available as a partm
ial means for the control of the black bullhead population and for the benefits to anglers
inherently derived from the presence of this species.
Sense F‘ Wiisex._ . Approved by .///3422rwpa* i» ca/x“ Marci
Prepared by it“; “a“-.. "in-.i,
Assistant Project Leader Director Inland Fisheries Division
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