TPWD 1963 F-6-R-10 #820: Fisheries Investigations and Surveys of the Waters of Region 5-B: Basic Survey and Inventory of the Fish Species Present in the San Antonio River, Job Completion Repor
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JOB COMPLETION REPORT
As required by
FEDERAL AID IN FISHERIES RESTORATION ACT
TEXAS
Federal Aid Project No. F-6-R-10
FISHERIES INVESTIGATIONS AND SURVEYS OF THE WATERS OF REGION 5-B
Job No. B-18 Basic Survey and Inventory of the Fish Species Present
in the San Antonio River
Project Leader: Charles T. Menn
H. D. Dodgen
Executive Secretary
Texas Game and Fish Commission
Austin, Texas
Marion Toole
D-J Coordinator Eugene A. Walker
Director, Program Planning
February 4, 1963
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ABSTRACT
The basic survey of the San Antonio River lying within Wilson, Karnes, Goliad
and Refugio counties revealed that channel and flathead catfish are the principal
game species. For that reason, every effort should be made to protect and propa-
gate catfish in this drainage.
Soil pollution over many years has caused the formation of silt deposits
along the banks of the relatively narrow river, which tend to favor "rough fish."
Rough fish species including alligator, spotted and longnose gars, gizzard
shad, smallmouth buffalo, river carpsucker, carp, grey redhorse, and Rio Grande
perch comprised 84.16 per cent by number and 97.40 per cent by weight of the fish
taken in the netting collections.
Red shiners were found at all 15 seining stations and comprised 42.97 per
cent of the fish taken in the seining collections.
No recommendations are made for developmental work at this time. However,
reconnaissance checks should be made at least once a year to detect gross changes
in fish populations.
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JOB COMPLETION REPORT
State of Texas
Project No. F-6-R-10 Name: Fisheries Investigations and Sur-_
veys of the Waters of Region 5-B
Job No. B-18 Title: Basic Survey and Inventory of the
Fish Species Present in the San
Antonio River
Period Covered: January 1, 1962 through December 31, 1962
Objectives:
To determine the physical, chemical and ecological conditions and
the relative numbers of fish species present in the lower portions of
the San Antonio River lying within Wilson, Karnes, Goliad and Refugio
Counties.
Procedure:
Maps prepared by the Texas Highway Department were used in the field
to pinpoint seining, netting and water sampling stations. Tracings of U.S.
Department of Agriculture aerial photographs were mot made because of their
large size. The project leader decided that such maps would not be practical
for this work and that the expense of tracing the maps would not be
justifiable.
Notes were made of pollution, aquatic vegetation and other ecologi-
cal factors.
The fish populations were sampled with the standard, 125-foot long,
gill nets and nylon minnow seines. The gill nets are constructed of nylon
webbing, 8-féet deep, in five 25-foot long sections of 1-, 1}-, 2-, 2%,-
and 3- inch square mesh. Specimens taken in the nets were weighed in grams
and measured in millimeters in the field. Internal examinations were made to
determine sex, stage of sexual development and incidence of parasitism.
Stomachs of carnivorous species were examined to determine food habits.
Seined specimens were preserved in 10 per cent formalin and taken to
the Mathis field office for identification and tabulation.
A list of the fish species taken in nets and seines is included in
Table 1.
The scientific and common names used in this table were taken from Hubbs'
A Checklist of Texas Fresh-Water Fishes, Texas Game and Fish Commission, IF
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Table 1. A List of Fish Species Recorded From San Antonio River
a
Common Name
Scientific Name.
ELS
Alligator gar
Spotted gar
Longnose gar
Threadfin shad
Gizzard shad
Mexican tetra
Smallmouth buffalo
River carpsucker
Grey redhorse
Carp
Golden shiner
Pugnose minnow
Speckled chub
Red shiner
Ghost shiner
Bullhead minnow
Channel catfish
Yellow bullhead
Flathead catfish
Tadpole madtom
Blackstripe topminnow
Mosquitofish
Sailfin molly
Striped mullet
Tidewater silverside
Largemouth bass
Warmouth
Green sunfish
Redbreast sunfish
Bluegill
Longear sunfish
Logperch
Rio Grande perch
Lepisosteus spatula Lacepede
L. oculatus (Winchell)
L. osseus (Linnaeus )
Dorosoma petenense (Gunther)
D. cepedianum (LeSueur)
Astyanax mexicanus (Filippi)
Ictiobus bubalus (Rafinesque)
Carpiodes carpio (Rafinesque)
Moxostoma congestum (Baird and Girard)
Cyprinus carpio Linnaeus
Notemigonus crysoleucas (Mitchill)
Opsopoeodus emiliae Hay
Hybopsis aestivalis (Girard)
Notropis lutrensis (Baird and Girard)
N._buchanani Meek
Pimephales vigilax (Baird and Girard)
Ictalurus punctatus (Rafinesque)
I. natalis (LeSueur)
Pylodictus olivaris (Rafinesque)
Schilbeodes gyrinus (Mitchill)
Fundulus notatus (Rafinesque)
Gambusia affinis (Baird and Girard)
Mollien¢sia latipinna (LeSueur)
Mugil cephalus (Linnaeus
Menidia beryllina conan
Micropterus salmoides (Lacepede)
Chaenobryttus gulosus (Cuvier)
Lepomis cyanellus (Rafinesque)
L. auritus (Linnaeus)
L. macrochirus (Rafinesque)
L. megalotis (Rafinesque)
Percina caprodes (Rafinesque)
Cichlasoma cyanoguttatum (Baird and Girard)
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Series No. 3, June 1961.
Findings:
Physical Description
The San Antonio River rises within the City of San Antonio and flows
approximately 180 miles in a southeasterly direction to its confluence
with the Guadalupe near San Antonio Bay on the Texas coast. With a relative-
ly small watershed of only 4,460 square miles and a semi-arid climate, the
mean annual flow of the river near its mouth is a meagre 350,000 acre feet.
The major tributaries of the San Antonio are the Medina River and
Cibolo Creek. Both are spring fed streams and differ somewhat in water
quality from the San Antonio, particularly in turbidity.
Normally the San Antonio River is a rapidly moving, turbid stream
with an average width of some 40 feet and an average depth of five feet.
In the portions of the river included in the study, the banks are mostly
sharply cut, indicating frequent flooding. The stream bottom varies from
limestone, in Wilson County, to sand and sandstone in Karnes and Goliad
counties to sand, sandstone and mud in the lower portions of Refugio County.
Silt deposits are found near the banks along the river, but are lacking
in the main current.
Pecan, hackberry, ash, cottonwood and cypress trees are numerous along
the river. Also, willow, huisache and mesquite trees are frequently encoun-
tered along the San Antonio. Bloodweeds, grapevine, sunflowers and prickly
pear combine to form dense thickets lining a considerable part of the river.
Netting Collections
Five netting stations were set up during this survey; three on the San
Antonio River and two on Cibolo Creek. The netting stations on the creek were
located in Wilson County and those on the San Antonio River were in Karnes,
Goliad and Refugio counties. No suitable netting water on the San Antonio
River was found in Wilson County. An overnight set was made at each station
twice during the study period.
All told, 120 fish of 17 species weighing 215.2 pounds were taken in
the netting collections. Game fish species including channel catfish,
flathead catfish, largemouth bass, warmouth, bluegill, redbreast and long-
ear sunfish comprised 15.84 per cent of the netted fish and 2.60 per cent of
their weight.
Rough fish species including alligator, spotted and longnose gars,
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gizzard shad, smallmouth buffalo, river carpsucker, carp, grey redhorse,
and Rio Grande perch dominated the netting collections both in numbers and
in weights with 84.16 per cent of the number and 97.40 per cent of the weight.
Tables 2 and 3 show the results of netting by station.
Gars of one species or another were taken at all stations, but were
more abundant in the lower portions of the river in Goliad and Refugio counties.
Unidentifiable fish remains were found in four gar stomachs and five were
empty. No parasites were found.
Gizzard shad were taken only at Station No. 3, at Conquista Park in
Karnes County, and at station No. 5, near the mouth of the San Antonio River
in Refugio County. The shad comprised only 6.67 per cent of the number and
3.67 per cent of the weight of the fish netted. The relatively small shad
population is probably due to the abundance of predators such as gars and
catfish.
Collectively, smallmouth buffalo, river carpsucker and grey redhorse
comprised 35.83 per cent by number and 25.65 per cent by weight of the fish
taken in the netting collections. Of the three species, smallmouth buffalo
appear to be dominant in the lower portions of the river, while grey
redhorse are limited to the clearer waters of Cibolo Creek and probably to
the clearer, upper portions of the river.
It is interesting to note that only one specimen of carp was taken
during the survey. The lone carp was taken at netting Station No. 3, at
Conquista Park in Karnes County. A state fisheries survey made in 1953
by Kuehne (IF Report Series No. 1, Texas Game and Fish Commission) also
found that carp were lacking in the San Antonio basin , Thus,it appears that
the San Antonio River is one of the few drainages in the state lacking a
sizeable carp population.
Rio Grande perch were taken only at the Conquista Park netting stations
in Karnes County. However, this species was taken in several seining collect-
ions in the upper portions of the river and in Cibolo Creek. Apparently
cold water during winter months controls their numbers in downstream areas,
since none were taken in either nets or seines. Apparently spring areas in
the upper portions of the river and in Cibolo Creek afford sufficient
protection for their survival.
The largemouth bass, in this drainage, appears to be limited to the
upper portions of the San Antonio River and to Cibolo Creek. Only three
specimens were collected in netting collections and this occurred at the
Conquista Park site. Murky water apparently prevents development of a good
bass population in most of the river. To offset poor reproduction of the
species, 11,000 largemouth bass fingerlings were stocked during May 1962 in
areas of Cibolo Creek where sufficient food and cover were available.
Channel catfish and flathead catfish seem to be well established in
the river. Only four channel and flathead catfish were taken in the nets,
but 127 channel catfish were taken in seining collections at various places
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along the river and Cibolo Creek. Insect remains were found in a channel
catfish's stomach.
Table 4 shows the length-weight statistics for fish taken in netting
collections. The "K" factors of all fish were considered better than
average, indicating that they are in good condition.
Seining Collections
Originally 20 seining stations were planned, but only 15 suitable sites
were found. Eleven stations were located at various places on the San Antonio
River in Wilson, Karnes, Goliad and Refugio Counties, and four stations were
located on Cibolo Creek in Wilson County. For the most part, the stations
were set up near road crossings to facilitate access. They represented
various types of habitat. Two collections were made at each station during
the study period.
In all, 4,012 specimens of 21 species were taken in the 30 seining
collections. Table 5 shows the number of each species recorded at each
station.
The red shiner is the most abundant fish and best distributed in the
San Antonio River, as well as Cibolo Creek. This minnow was taken at every
station and comprised 42.97 per cent of the fish seined.
Mosquitofish, pugnose minnows, channel catfish, bullhead minnows and
Rio Grande perch, in that order, were found to be well distributed through-
out the river system and in lower Cibolo Creek.
Mexican tetras, speckled chubs, blackstripe topminnows and logperch
were limited to the upper portions of the river, while threadfin shad,
striped mullet and tidewater silversides were found only in the lower
portions of the San Antonio.
Six grey redhorse were taken at a station on Cibolo Creek. This was
the only place where this species was taken, although we suspect them to
be present in good numbers in the creek.
Eight largemouth bass specimens were taken at a seining station on
the San Antonio River at Conquista Park. Thus reproduction, although some-
what limited, is indicated. Under present conditions, primarily the high
turbidity and silt, it is doubtful that a good bass population can become
established in the river. Largemouth bass fingerlings were stocked in the
clearer waters of Cibolo Creek in May 1962 to supplement the existing
population. Sufficient food in the form of red shiners and cover were found
in the creek. Therefore, these bass should be helpful in restoring that
species.
Neither species of crappie was taken in either netting or seining
collections. This seems rather odd since a number of areas appeared
to be suitable for this species. The absence of crappie during this survey
is in line with Kuehne's study in 1953.
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Chemical Analysis
Six water sampling stations were set up during this survey; four were
on the San Antonio River and two were on Cibolo Creek. Each station was
visited twice during the survey.
Surface water samples were tested for dissolved oxygen, dissolved
carbon dioxide, total alkalinity and pH.
Dissolved oxygen ranged from 4.8 to 7.0 p.p.m. on the San Antonio River
and dissolved carbon dioxide ranged from 1.4 to 8.0 p.p.m. Methyl orange
alkalinity values ranged from 136 to 206 p.p.m. and pH ranged from 7.7 to 8.4.
All these values are considered normal for this area and are in line with
previous findings.
Water quality of Cibolo Creek is similar to that of the San Antonio
River with the exception of turbidity. Secchi disc readings ranged from 3-
to ll-inches on the river and from 15- to 17-inches on Cibolo Creek.
During the course of this job, an investigation was made to determine
the cause of a fish kill on the river in Wilson County, Since the investigation
was made two days after the fish kill was reported, it was difficult to make
an accurate estimate of the fish kill. No dead fish were seen along the river
channel. However, in one slough, approximately 300 feet in length, there were
some 20 smallmouth buffalo, 80 carp and 100 channel catfish. The fish had
been dead for at least a day. Water samples were taken from the slough and
tested for dissolved oxygen, dissolved carbon dioxide, pH and methyl orange
alkalinity. All were considered normal and no definite cause for the fish kill
could be determined.
Ecological Conditions
Rainfall in the San Antonio River basin ranges from about 27 inches in
the western portion to about 34 inches near the coast.
Aquatic vegetation in the San Antonio River consists mostly of algae
clinging to limestone, Water pennywort was found along the banks of pool
areas and a small amount of Lemna sp. was found in the still, backwater
areas, Due to the nature of the river in Wilson, Karnes and Goliad Counties,
aquatic vegetation is not a problem and is not likely to become one under
present conditions.
Spatterdock, algae, water pennywort and arrowhead comprised the
aquatic forms of vegetation in Cibolo Creek, However, none of these is
considered undesirable in the creek because of the protection they offer
fish and aquatic invertebrates, Most likely winter-kills control the plants.
A limited amount of ranching is done in the vicinity of the river in
Wilson and Karnes Counties, However, the trend is toward row crops and truck
farming, In areas along the lower portion of the river, the land is hilly and
farming is unprofitable.
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Good soil conservation measures have been used, but more are needed
in the form of terracing, planting cover crops and not overgrazing pasture
land.
No nutria were found along the river nor was there any evidence indicat-
ing their presence.
Discussion:
Presently the portion of the San Antonio River studied during this
segment has little potential for largemouth bass production. This is due
to the silt and turbidity. It was reported that the river supported a
sizeable bass population in previous years.
The catfish are the only significant game fish species in the river.
Despite the rather low numbers taken in netting collections, sufficient
evidence was found to indicate a moderate population in the river. Further-
more, it is apparent that the catfish are reproducing successfully.
Both largemouth bass and channel catfish were stocked in the lower
portion of Cibolo Creek in Wilson County. These fish should do well in this
relatively clear stream which offers ample food and cover.
Only 19 sport fishermen were seen during the course of this job. Most
of them were seen on Cibolo Creek, however. In nearly every case, the
anglers were fishing for catfish and they offered stories of good catches
on previous trips.
Public access is limited to road crossings, both on the river and
Cibolo Creek. Many landowners are accommodating to those who ask permission
to fish on posted areas.
At least two major dams are proposed for the San Antonio River; one
is to be located near Falls City in Karnes County and the other near Charco
in Goliad County. Undoubtedly these proposed impoundments would be an asset
to the basin in that they would provide water storage and help control floods.
Presently there are no fishing camps located along the river or Cibolo
Creek,
Recommendations:
Every reasonable effort should be made to stop industrial, municipal
and soil pollution on the river. This, of course, would require the combined
efforts of many people and agencies, and much time for the river to revert
to its original state. We have every reason to believe that the San Antonio
River was at one time a beautiful stream, as reported.
The sports fishermen will be forced to fish for catfish in the river.
Cibolo Creek has a moderate population of largemouth bass in addition to a
good catfish population. Since the catfish is one of the principal game
Species in the San Antonio River system, commercial fishermen should not
be allowed to take them and every effort should be made to protect and
propagate them.
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t
Annual checks should be made on the river to determine gross changes
in fish populations.
No developmental work is presently proposed or recommended.
: —
Prepared by Charles T. Menn Approved by Yi OVE Ao ce
‘ Coordinator
Date February 4, 1963 Kenneth C. Jurgens
Fisheries Supervisor, Region V