TPWD 1954 F-5-R-1 #65: Inventory of species present and their distribution in those portions of the Middle and South Concho Rivers occuring within Tom Green, Reagan, Irion and Schleicher Count
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. STATE _tsti‘“t;‘*CS KAS
PROJECT NO, F-5-R-1, Job B-6
PERIOD June 22, 1953 - June 12, 195)
Job Completion Report
Lawrence Campbell
TITLE
Inventory of species present and their distribution in those portions of the Mid-
dle and South Concho Rivers occuring within Tom Green, Reagan, Irion and Schleicher
Counties, Texas.
To determine distyiibution of species present, their relative abundance, and the
ecological factors influencing their distribution.
METHODS
Forty-seven seining collections were made at fifteen locations on the South and
Middle Concho watershed. In nearly all collections both 26 ft. y" mesh bag seines and
15 ft. $" mesh common sense seines were used. To estimate relative abundance a count
was made of all individuals taken in sixteen collections. Four collectims were taken
in each type stream habitat, and the resulting data analyzed on a seasonal basis. In
other collections data pertaining to species distribution only was recorded and in
addition to the above equipment, six ft. and four ft. common sense seines and 1/8"
mesh fry seines were employed.
Sixteen gill net collections were made. Experimental nylon gill nets measuring
125 ft. x 8 ft. in depth and made up in five, 25 ft. sections, were set at eight sta-~
tions. Mesh size for these nets increased progressively in each following section at
one-half inch intervals beginning with 1" mesh and terminating with a 3" mesh section.
Three rotenone collections were made, one for each stream sub- division. Data
pertaining to numerical and weight percentage was taken for each species recovered and
the volume of water treated estimated. :
in all eollections most of the fish taken were identified and counted in the field.
However, some individuals whose identity was questionable were preserved in 10% forma-
lin and a sample of each species was saved for a laboratory collection.
PINDINGS
For reasons discussed in the Completion Report for Job A-1, it is considered de-
sirable to report distribution and abundance of species data under titles used to de-
note the three ecological associations found in the watershed.
1. Spring fed, permanent flow, clear water association. (Description and dis-
cussion in report for Job A-l. Shown on map stations 5, 10, 11 and 12)
Seining Collection Results
A. Spring areas (Stations 5 and 10)
Estimations based on total counts for four seasnnal collections.
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Species Number Total %
l. Moxostoma congestum L a
2. Campostoma anomalum 38 10.9
3, Gambusia affinis 113 32.7
4, Pimephales vigilax 27 7.8
5. Etheostoma spectabile 31 8.9
6. Notropis buchanani 12 3.6
7. Notropis amabilis 11 3.2
8, Notropis venustus 18 2
9. Lepomis cyanellus AL 11.8
10. Lepomis megalotis 21 6.1
11. Lepomis auritus 2h. 6.9
12. Lepomis macrochirus 2 5
13. Lepomis microlophus 2 aD
14. Pomoxis annularis 2 25
15. Chaenobryttus coronarius hh 1.2
Totals 317 100.1
B. Clear water, permanent flow areas below springs. (Stations 11 and 12)
Estimate based upon four seasonal collections.
Species Number Total %
1. Dorosoma cepedianum 54 6.5
2. Moxostoma congestum 36 3
3, Carpiodes carpio 18 2.2
4. Campostoma anomalum 63 7.5
5. Pimephales vigilax 61 7.3
6. Notropis venustus 121 W.5
7. Notropis lutrensis 183 22.0
8. Houzopie percobromus 4 05
9. otropis amabilis 9 1.1
10. Micropterus salmoides 3 4
ll. Micropterus punctatus 05
le. Chaenobryttus coronarius 9 1.1
13. Lepomis cyanellus 114 13.7
ik. Lepomis megalotis 61 7.3
15. Lepomis macrochirus 6h. 7.6
16. Lepomis mierolophus 13 1.6
L7. Lepomis auritus 2 2
18. Pomoxis annularis 12 1.4
L9. Iectalurus punctatus 2 62
20. Pilodictus olivaris 1 Ji
Totals 834. 100.2
Netting Results
A. Wetting in spring fed, clear water, permanent pools created by Stil--
son and Christoval Dams (Stations 11 and 12). Estimate based on six
netting collections.
Species Number Total Weight % by Number 4% by Weight
los. OZS.
Dorosoma cepedianum 115 58 10 4O.2 15.9
Carpiodes carpio 60 216 0.0 2160 57.5
Moxostoma congestum 32 64 O60 11.2 17.1
Aplodinotus grunniens 12 3 2.0 4.2 8
Lepisosteus osseus i" 12 1.0 6.3 3.3
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Species Number Total Weight % by Number % by Weight
ibs. OZS ©
Pilodictus olivaris 2 4 6.0 aT 1.0
Micropterus salmoides 4 4 1.0 Lat 1.0
Ietalurus punctatus 6 9 8.0 2 ol 1.0
Lepomis sp. 34 4 8.0 11.9 5
Pomoxis annularis 3 Te) 1.1 me)
Totals 286 376 8.0 100.0 100.5
Rotenone Collection
A. Collection by rotenone made approximately two miles northeast of
Station 8. Area treated approximately .25 acre ft.
Species Number Total Weight % oy Number % by Weight
ios. OZS.
Dorosoma cepedianum 13 1 1 8.3 5.5
Micropterus salmoides 20 1 4 12.5 6.3
Tetalurus punctatus 5 1 5 3.2 Ga F
Chaenobryttus coronarius 3 0 2.0 2.3
Lepomis cyanellus 29 4 7 17.6 22.6
Lepomis macrochirus 26 3 2 16.0 15.8
Lepomis megalotis 14 4 1 9.0 20.5
Lepomis auritus 4 11 2.6 3.4
Lepomis humilis 3 7 3.1 2.4
Lepomis punctatus 3 6 3.1 1.9
Lepomis microlophus 14 1 \. 9.1 6.3
Hybrid sunfishes 9 1 2 5.8 5.7
Gambusia affinis 12 2 Tel 6
Totals 155 19 13 100.0 100.5
Orangethroated darters (Etheostoma spectabile) were in spring areas only.
Such spring communities were dominated by small plankton feeders and by sun-
fishes. In other clear water associations, sunfishes averaged 32% of the
total for all type collections. Green sunfish (Lepomis cyanellus) and west-
ern lonear (Lepomis megalotis}) were more abundant and have the greatest area
of distribution. However, yellowbelly sunfish (Lepomis auritus) and warmouth
bass (Chaenobryttus coronarius) were often larger and are preferred by fish-
ermen. Bluegill (Lepomis macrochirus) were the more abundant species in larg-
er pools, especially where aquatic vegetation was heavy. These fish usually
appear to be stunted. Common mosquitofish (Gambusia affinis) were the most
abundant species taken and were in all localities where a swift stream flow
was not prohibitive. These fish were especially numerous in shallow backwaters.
Blacktail shiner {Notropis venustus) and red shiners (Notropis lutrensis) were
concentrated in swifter water and in the deeper pools below riffles. Below
springs, in clear water associations where there was appreciable current, giz-
gard shad {Dorosoma cepedianum) and gray redhorse suckers (Moxostoma congestum)
increased in numbers and may possibly be the dominant species in some communi-
ties. Downstream as transition into murky water association occurs and in ir-
rigation reservoirs, river carp suckers (Carpiodes carpio) become more abundant
over Moxostoma.
lil. Murky Sluggish Flow Association
Seining Collections
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Near impoundments on Spring and Dove Creek and on the South Concho near Christ+
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oval Dam and Gardner Dam (Stations 7, 8, 9, 13, 14 and 15). Estimates based on
four seasonal collections.
Species Nunber % Total
Lepisosteus osseus 5 of
Dorosoma cepedianum 31 4.3
Carpiodes carpio et 3.7
Moxostoma congestum 2 3
Cyprinus carpio 2 a3
Ictiobus bubalus 6 6
Aplodinotus grunniens y 26
Notemigonus chrysoleucas 13 dott
Pimephales vigilax 22 320
Percina caprodes 18 2.5
Hybognathus placitus 14 1.9
Gambusia affinis 1h0 19.3
Notropis yvenustus 112 15.5
Notropis lutrensis WL 5.7
Tetalurus punctatus 5 7
Ameiurus natalis el 2.9
Ameiurus melas 3 ob
Morone chrysops 11 1.5
Micropterus salmoides il Lie 5
Micropterus punctulatus L al
Lepomis megalotis 67 9.3
Lepomis cyanellus 33 5
Lepomis microlophus 27 3.7
Lepomis auritus 7 1.0
Pomoxis annularis 61 8.4
Lepomis macrochirus KL 5.7
Totals 725 100.1
Netting Collections
Impoundments on Spring and Dove Creek and South Concho River (Stations 7, 9,
13, 15}. Estimate based on six seasonal collections.
Species Number Total Weight % by Number % by Weight
lbs. OZS.
Doroxoma cepedianum 145 90 9 51.5 37.3
Carpiodes carpio LO 8h 0 1h.2 ah . 7
Moxostoma congestum 18 31 8 6.4 12.8
Aplodinotus grunniens 10 4 2 3.6 1.6
Lepisosteus osseus 4 10 2 1.4 i)
Pilodictus olivaris 3 9 2 Lead 367
Ietalurus punctatus 4 4 8 1.4 1.7
Pomoxis annularis 6 1 1 2.1 4
Micropterus salmoides 1 1 4 wl Jy
Morone chrysops 13 3 9 Ta 1.3
Sunfishes 37 h 2 13.2 Lf
Totals 281 2he 15 99.9 99.8
Rotenone Collections
Pool treated located approximately one mile from Station 15. Area treated
about 1.5 acre ft.
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Species Number Total Weight % by Number % by Weight
Lbs. Oz.
Dorosoma cepedianum 123 LO 3 15.4 30.4
Carpiodes carpio 21 36 @) 2.6 27.5
Moxostoma congestum 11 14 2 1.4 10.5
Aplodinotus grunniens 4 1 0 5 -7
Cyprinus carpio 12 4 9 1.5 3. 3
Ietalurus punctatus 14 6 2 1.5 HOS
Pilodictus olivaris 4 7 3 25 5.3
‘Micropterus salmoides 8 4 0 9 3.5
Pomoxis annularis 9 3 2 1.4 2.2
Sunfishes 102 14 1 12.6 10.4
Small forage fishes* 500 3 11 61.6 2.2
Totals 818 133 L 100.0 100.4
* . Estimated number for genus Notropis, Hybognathus, Gambusia and Pimephales.
The greatest number of species found in any association in the watershed occur in
Most of these pools are created by reservoir impound-
ments and Blacktail shiners (Notropis venustus) and Red shiners (N. lutrensis) were
usually found in the upper portions of such pools and were numerous below the water
murky sluggish flow assodations.
outlet.
cate that gizzard shad (Dorosoma cepedianum) as the most important forage species.
fishes, especially green sunfish and western longears, are common and bullheads (Ameiu-
rus and A. melas), log perch (Percina cap rodes) and flathead catfish (Pilodictus oli-
varis) were taken only in this habitat.
IIL. Silty Intermittant Pool Association.
Description and discussion in report for Job A-l.-
Turbid, intermittent pools at Stations 2 and 3.
Seining C
ollections
collections.
Species Number % Total
Dorosoma cepedianum yh 11.5
Carpiodes carpio 61 16.0
Cyprinus carpio 37 9.7
Aplodinotus grunniens ” 1.8
Gawbusia affinis 111 29.8
Notropis venustus 25 6.6
Notropis ‘lutrensis 32 8.4
Notemigonus crysoleucas 6 1.6
Lepomis cyanellus 31 8.1
Lepomis megalotis 14 3.7
Morone chrysops 4 1.0
Lepomis macrochirus 7 1.8
Ictalurus punctulatus L 3
Micropterus salmoides 2 s3
Totals 382 100.1
(Appended map stations 1,2 & 3
Eatimate based on four seasonal
Netting results, rotenone collections and stomach analyses of game fish indi-
Sun-
Rotenone Collections
Pool location approximately 3/4 miles southwest of Station 3. Area treated
approximately one acre ft.
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ON
Species Number Total Weight % by % by
Lbs. Ozs. No. Wt.
Dorosoma cepedianum 37 11 0 14.50 4.6
Carpiodes carpio 76 gu 9 28.80 37.0
Cyprinus carpio 22 78 8 8.64 31.7
Tetiobus bubalus 4 12 fo) 38 4.8
Aplodinotus grunniens ai 27 0 30.00 10.8
Moxostoma congestum 4 7 4 1.57 2.8
Ictalurus punctatus 2 3 4 .78 #1.7
Sunfishes 33 7 2 12.72 2.8
Totals 255 2hg 12 100.16 99.9
Gill nets were not set in this type association because suitable netting sites were
not available.
Although largemouth bass (Micropterus salmoides), white bass (Morone chrysops),
blacktail shiners (Notropis venustus) and red shiners (Notropis lutrensis) were
taken in this habitat, their presence is attributed to entrapment, recession of
the flowing stream to an intermittent pool condition. Mosquitofish (Gambusia
affinis) and freshwater drum (Aplodinotus grunniens) appear capable of adapting to
this environment. Green sunfish (Lepomis cyanellus) and bluegill (L. macrochirus )
are not uncommon. However, a complete dominance of this association by river carp
suckers (Carpiodes earpio), longnose gar (Lepisosteus osseus) and gizzard shad
(Dorosoma cepedianum) is overwhelming.
SUMMARY
1. Field work for this job was done in conjunction with Job A-l. (Basic Survey of
the South and Middle Concho Rivers.)
2. Forty-seven seining collections were made at fifteen stations, sixteen gill net
ecoOllectims were taken and three pools were treated with rotenone.
3. A total of 39 species from ten families were taken by all methods of collect-
ion for the entire watershed.
4. Three ecological associations were found to exist and seining, netting and rot-
enone collection data was analyzed on that basis.
5 Spring bed, permanent flow, clear water associations were dominated by sunfishes,
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especially green sunfish and western longear sunfish and by small plankton feeders.
6. The greatest number of species found were in murky sluggish flow associations
and most communities were dominated by river carp suckers. However, game species were
more numerous than in intermittent pool associations and were probably larger in aver-
age size.
7. Silty intermittent pool associations were characterized by an overwhe!ming dom-
inance of all species by river carp suckers and carp. Few game fish were taken in col-
leetions and conditions often Indicated that survival of all game fishes, excepting sun-
fishes, was unlikely.
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Checklist of Fish Specie
Concho Rivers, July 22,
Common Name
Longnose gar
Gizzard shad
Smallmouth buffalo
Black buffalo
River carpsucker
Gray redhorse sucker
german carp
Golden shiner
Plains shiner
Blacktail shiner
Red shiner
Texas shiner
Mimic shiner
River shiner
Ghost shiner
Plains minnow
Parrot minnow
Flathead minnow
Southern channel catfish
Black bullhead
Yellow bullhead
Flathead catfish
Common mosquitoPish
White bass
Spotted black bass
Largemouth black bass
Warmouth bass
Green sunfish
Spotted sunfish
Redear sunfish
Bluegill
Orangespotted sunfish
Yellowbelly sunfish
Western longear sunfish
White crappie
Logperch
Orangethroat darter
Freshwater drum
Hybrids
Lepomis macrochirus x L. punctatus
Lepomis Kumilis x L. cyanellus
rom South and Middle
3 + June 12, 1954
Scientific Name
Lepisosteus osseus
Dorosoma cepedianum
etiobus bubalus
Ietiobus niger
Carpiodes carpio
Moxostoma congestum
Cyprinus carpio
Notemigonus crysoleucas
Notropis percobromus
Notropis venustus
Notropis lutrensis
Notropis amabilis
Notropis volucellus
Notropis blennius
Notropis buchanani
Hybognathus placitus
imephales vigilax
Pimephales promelas
Ietalurus punctatus
Ameiurus melas
Ameiurus natalis
Pilodictus olivaris
Gambusia affinis
Morone chrysops
Micropterus punctulatus
Micropterus salmoides
Chaenobryttus coronarius
Lepomis cyanellus
Lepomis punctatus
Lepomis microlophus
Lepomis macrochirus
Lepomis humilis
Lepomis auritus
Lepomis megalotis
Pomoxis annularis
Percina caprodes
Etheostoma spectabile
Aplodinotus grunniens
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