TPWD 1954 F-5-R-1 #70: Inventory of Species Present in Lake Nasworthy: Job Completion Report, Project F-5-R-1
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STATE noone 7
PROJECT NO, F-5-R-1, Job B-l
PERIOD June 22, 1953 - June 22, 1954
Job Completion Report
Lawrence S. Campbell
TITLE
Inventory of Species Present in Lake Nasworthy.
OBJECTIVES
To determine the species present and their relative abundance and to determine
the ecological factors influencing their distribution.
PROCEDURE
Forty-eight gill nets were set for twelve collections. Experimental nylon gill
nets measuring 125 ft. long by eight ft. deep and made up in five, 25 ft. sections were
used. Mesh size for these nets increased progressively in each following section at half
inch intervals beginning with a one-inch mesh section and terminating with a three-inch
mesh section.
Twenty-four seining collections were made at eight seining stations in the reser-
ir. In nearly all collections both 26 ft., $" mesh bag seines and 15 ft., ¢" common
sense seines were used. To estimate relative abundance a count was made of all individ-
uals taken in two hauls with a 26 ft. i" bag seine. In addition to this work, collections
with 4 ft. common sense 1/16" mesh fry seines were taken.
Water analysis to determine dissolved carbon dioxide and oxygen content was tak-
en for each netting collection and surface temperature, pH and the climatic conditions
were recorded for each netting and seining collection. Turbidity was taken on six occas-
ions.
In netting collections, samples from each collection and for each species were
weighed, measured and sexed. This work was done in the field. A scale sample was taken
from a sample number of individuals for each species and stomachs containing food were
preserved for laboratory analysis. Similar work for seining collections included ident-~-
ification, weighing and measuring and the preservation of all indivuals whose identify
was questionable in 10% formalin.
PINDING
Lake Nasworthy is located approximately 6.5 miles southwest of the City of San
Angelo. The dam creating this reservoir is one-fourth mile below the confluence of the
Middle and South Concho Rivers, is an earth fill construction with concrete retaining
gates and is 5,480 feet long. The reservoir was created by the Upper Colorado River Auth-
ority and has been sold to the City of San Angelc. The impounded water is used exclus-
sly for municipal and industrial consumption. When the lake is at emergency spillway
vel it has about 1,300 surface acres and contains about 14,040 acre feet of water. At
that elevation the lake has about 28 miles of shoreline.
The contributing watershed of 2,659 square miles is San Angelo Sandstone forma-
tion and top soils are usually Abeliene sand or Frio clays and loams. The vegetative cover
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2.
is mesquite-grassland association and the area is currently employed in farming and ranche
g. The climate is semi-arid, having annual average rainfall of 19.7 inches. The aver-
uge annual discharge for the South and Middle Concho Rivers is 162 c. f. s.3; however, a
maximum flow of 230,000 c. f. s. was recorded in September, 1936 and recent annual dis-
charles have been 1.62 c. f. s. in 1952 and 50.le. £f. s. in 1953.
The lake's water is usually turbid (12 to 18); the maximum carbon dioxide content
recorded was 14 ppm and the minimum dissolved oxygen content recorded at that time was 3
ppm. Dissolved carbon dioxide was usually about 8 - 11 ppm and oxygen was usually about
5 to 8 ppm. pH for the reservoir was from 8.2 to 8.5.
NETTING RESULTS
Forty-eight experimental gill net sets resulted in the capture of 1,351 individ-
uals of 16 species. In Table ll, the numerical and weight dominance of river carp suckers
(Carpiodes carpio), gizzard shad (Dorosoma cepedianum), carp (Cyprinus carpio) and long-
nose gar (Lepisosteus osseus) is adequately demonstrated. However, the latter species may
be less numerous than indicated. White bass (Morone chrysops) and southern channel cat-
fish (Ictalurus punctatus) appear to be dominant game species. In Table 1, failure of net-
ting to indicate significant population fluctuations for most species is interpreted as a
possible indication that little change in ratios has occured during the study period and
that under the conditions now existing the lake may be regarded as balanced.
SEINING RESULTS
Twenty-four seining collections were used in compiling the data for Table 111.
Fifteen species and 2,553 individuals were captured. In addition to that data, several
her species were taken in other collections where relative abundance estimation was not
attempted. Since Lake Nasworthy was not adequately cleared of woody vegetation prior to
inundation, seining stations were difficult to establish and rapid growth of bullrushes
(Scirpus sp.) and cattails (Typha latifolia) made reclearing necessary at some seining
stations. For those reasons percentages for some species may be erroneous, however appar-
ent trends toward increases in white bass, largemouth black bass (Micropterus salmoides)
and shiners (Notropis) may be indicative of gradual improvement in the lake condition.
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SUMMARY
do
2.
Forty-eight gill net sets were made at twelve locations. One thousand, three
hundred and fifty-one individuals of sixteen species were captured.
Twenty-four seining collections captured 2,553 individuals of fifteen species,
and additional species were obtained where relative subundance data was not
taken.
Water analysis showed dissolved carbon dioxide content to be from 9 to 14 ppm
and dissolved oxygen to be from 3 to 11 ppm. pH was from 8.2 to 8.5, arid tur-
bidity 12 to 18,
Dense aquatic vegetation in the upper lake and near the mouth of the South Con-
Concho River has extremely rapid growth on shallow flats. This vegetation is
primarily bullrushes (Scirpus sp.), pondweeds (Potomogeton natans and P. spir-
illus) and cattails (Typha latifolia).
It is concluded that netting results may error in actual percentages but the
dominance of the lake by river carp suckers, carp, gizzard shad and longnose
gar is adequately demonstrated.
Seining results may error in the percentages for some species but trends indi-
cate a general improvement in the lake condition.
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oO wAY ON
18.
19.
20.
Checklist of Species of Fish from Lake Nasworthy
June 22, 1952 to June 22, 1954
Common Name
Longnose gar
Gizzard shad
River carpsucker
German carp
Gray redhorse sucker
Golden shiner
Blacktail shiner
Red shiner
Texas chhiner
Parrot minnow
Southern channel catfish
Flathead catfish
common mosquitofish
Largemouth black bass
Warmouth bass
Green sunfish
Spotted sunfish
Redear sunfish
Bluegill
Orange spotted sunfish
Yellowbelly sunfish
Western longear sunfish
White crappie
Logperch
Freshwater drum
Scientific Name
Lepisosteus osseus
Dorosoma cepedianum
Carpiodes carpio
Cyprinus carpio
Moxostoma congestum
Notemigonus crysoleuvcas
Notropis venustus
Notropis lutrensis
Notropis amabilis
Pimephales vigilax
Ictalurus punctatus
Pilodictus olivaris
Gambusia affinis
Micropterus salmoides
Chaenobryttus coronarius
Lepomis cyanellus
Lepomis punctatus
Lepomis microlophus
Lepomis macrochirus
Lepomis humilis
Lepomis auritus
Lepomis megalotis
Pomoxis annularis
Percina caprodes
Aplodinotus grunniens
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Lake NaswortTHy
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COUNTY PARK