TPWD 1955 F-7-R-3 #125: A Basic Survey of and Inventory of Species in the Little Wichita River in North-central Texas, lying in the Counties of Baylor, Archer, and Clay
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WICHITA £iecEKe jel MLe
STATE Texas
PROJECT NO. F7R3, Jobs A-3 and B-O Combined
PERIOD June 1, 1955 to May 31, 1956
Job Completion Report
Leo D. Lewis, Project Leader
Walter Dalquest, Assistant Project Leader
TITLE
A Basic Survey of and Inventory of Species in the Little Wichita River in North-
central Texas, lying in the Counties of Baylor, Archer, and Clay.
OBJECTIVES
To gather fundamental data on the above waters in regard to their physical,
chemical, and biological aspects, and to determine the species of fishes present, as well
as the relative abundance and ecological factors influencing the distribution of such
fishes. ;
SCOPE
The entire length of the Little Wichita River is included in this report, from
headwaters to its confluence with the Red River of Oklahoma. Excluded is Lake Kickapoo,
the only major impoundment of the Little Wichita River at this time. The fisheries biology
of this reservoir has been previously reported (Completion Report F7R1, Job B-3, 1954.)
TECHNIQUES
Sample stations were established at six points along the length of the Little
Wichita River, at carefully selected localities between the headwaters of the stream and
its mouth. At these sample stations, chemical and physical data concerning the water
were taken monthly. Seine samples of the fishes present were preserved in formalin for
laboratory examination and identifications. At the two stations where the water was deep
enough for the use of gill nets, and where seining could not give an adequate picture of
the fish populations, overnight net sets were maintained. The fishes taken in gill nets
were weighed and measured in the field. Ripe ovaries and filled stomachs of game fishes
were saved for laboratory examination. Pathological conditions were noted or, when
necessary, preserved in formalin for histological examination. On a few occasions fish
collections were made with the use of rotenone. Ecological data were obtained by “walking-
out" selected sections of the river. There are no important permanent-flowing tributaries
of the Little Wichita River.
ACKNOWLEDGMENTS
We wish to express here our appreciation to Dr. Carl Gray, Soils Scientist of
Midwestern University and the Wichita County Water Improvement Districts, for makeing the
numerous water analyses so important to this study.
INTRODUCTION
An accident of geology and the erosional history of Northcentral Texas has forced
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25
upon the Little Wichita River a role far more important tham its size would seem to
justify. Throughout most of its length the Little Wichita River is a narrow, muddy
intermittent stream, scarcely worthy of the designation "river." However, this stream
is virtually the only adequate supply of fresh water in an area of saline streams and
rivers so arid that water is at a premium. One large reservoir, Lake Kickapoo, exists
on the Little Wichita River at the present time, and another is to be constructed in the
very near future. Still others will doubtless be made later. The growing population of
the region and heavy fishing pressure demands a careful study of the river so that the
sports fisheries of the new lakes can be better managed for the public good.
BASIC SURVEY OF THE LITTLE WICHITA RIVER
The Little Wichita River is apparently of relatively recent origin. To the north
the Big Wichita River is entrenched nearly 135 feet deeper, on a course almost parallel
to tnat of the Little Wichita, while to the south the Brazos River also parallels the
Little Wichita and is cut some 50 feet deeper. In central Baylor County the Brazos
bends northward and the Big Wichita bends southward until these two rivers come to lie
quite close together. Between them they drain the land west of the sources of the
Little Wichita and limit the westward extent of. this stream.
This capture of the land west of the present Little Wichita River has two
important results. The Little Wichita is an intermittent stream, because the only per-
manently flowing springs in the area lie to the westward, beyond the drainage of the
Little Wichita River. The Little Wichita River is confined to a shallow valley cut only
into the Admiralty Formation of the Permian Wichita Group, and possibly near its mouth
into Cretaceous sediments. The entire valley of the Little Wichita is thus on non-marine
sediments, and the salt and gypsum beds of the younger, marine Permian rocks are to the
westward and are drained by the: Big Wichita and the Brazos. For this reason the waters
of the Little Wichita are "sweet" and suitable for human consumption and most fish life.
The Little Wichita River is a small stream, its straight-line length being only
about 75 miles. Its origin is a series of arroyos and a shallow but broad valley south
of the railroad station of Fulda, in eastern Baylor County. It follows a rather sinuous
course to the east-northeast to its confluence with the Red River of Oklahoma, in extreme
eastern Clay County. The total drainage area is approximately 1,000 square miles. A
major reservoir, Lake Kickapoo, is located near the headwaters of the Little Wichita, in
Archer County, and is the water supply of the city of Wichita Falls. Another and larger
reservoir is soon to be constructed on the lower part of the river, in Clay County.
Ecologically the drainage system of the Little Wichita River lies in the Mesquite
Plains Biotic Province, although some of the drainage area near the mouth of the river
is within the outlying groves of the post-oakS of the West Cross Timbers. The shores
and immediate environs of the river itself, however, are remarkably uniform and unlike
the arid mesquite-desert. The soil is usually a deep, rich humus or silt and supports
a rather dense vegetative cover of trees, especially elms and cotton woods with an
undergrowth of wild-plum, briars and other woody shrubs and vines. Only for a few miles
downstream from Lake Kickapoo Dam, where there is ordinarily no water flow, is the
broadleaf vegetation absent. There the dry river-channel is of sand and boulders and
adjacent vegetation consists of mesquite, palo-verde, cacti and other desert plants.
The Little Wichita River is but shallowly entrenched. The headwaters, west of
Lake Kickapoo, are cut through 12 to 15 feet of brownish gravel and soil and form a
channel rarely more than 25 feet wide and with vertical banks. Bones of Bison found
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in these gravels indicate a late Pleistocene or more probably Recent age, and prove the
relative youth of the Little Wichita River. The slot-like river channel is cut into a
broad, grassy valley, perhaps two miles wide at most, lying between exposed outcrops of
Permian sandstones. No terraces are apparent here and the valley seems to have been
formed by aluvium washed from the surrounding hills. The river bed is composed of sand
and small areas of gravel. Ordinarily the river is intermittent here, composed of a
series of larger or smaller pools separated by sandy reaches. During the study year
the headwaters were never completely dry, but this year was not especially arid for
the region. We suppose that in the past fifteen years, the headwaters have been dry
for years at a time except after rains. In times of heavy rain the river floods swiftly
and becomes a raging torrent. The river drains rapidly and within hours the flood
recedes, usually leaving only a series of disconnected pools in a matter of a few
days after the rains cease. Only where the river enters Lake Kickapoo is it permanent,
deep and sluggish as it flows between low, muddy banks.
The original nature of the river where now flooded by Lake Kickapoo is obscured.
The land surrounding the lake is high, composed of hills and areas of barren land.
Almost ali exposed land is Permian in age, with but thin and scattered areas of Recent
soils in level areas.
Below the Lake Kickapoo dam, the river is ordinarily a dry arroyo. Only twice
Since Lake Kickapoo was constructed has the lake overflowed its spillway. On those
occasions it ripped out a gash through the surface soils, exposing fifteen feet or more
of Recent soils and Pleistocene gravels. The age of the prairie soil is revealed by
numerous remains of Bison and human artifacts. The age of the gravels is established
by the remains of mammoth and camel. The bed of the river channel is Permian sandstone
and shale, covered with a thin layer of reworked sand and gravel. Some of the sand and
gravel of the lower reaches of the river may have originated here. Within four miles,
seepage and drainage fom pools in the river bed that remain for long periods after
rains, and some of these support fishes.
East of the Mankins-Archer City Road (State Hyghway 25,) the river assumes the
nature it maintains for most of the remainder of its length. The course is sinuous,
between broad, low hills. Trend is northeastward parallel to the Big Wichita River,
farther north. The river channel is a steep-banked, deep-sunken, "V-shaped" canyon,
usually about 40 feet deep and less than 100 feet across. The canyon is cut into deep
alluvium, washed from the surrounding hills. There is no evidence of terracing
or meandering. The course of the river valley is marked by a thin line of elms and
other broad-leafed trees, but the sudden drop into the canyon is not seen until one is
on the brink of the valley. The river remains a running stream through much of the
year, though only after rains is there any considerable volume of water. Usually the
water consists of a mere trickle connecting pools in the canyon floor. After a few
months without rains, even the trickles cease. Some of the deeper pools seems to
contain some water at all times. At least there are some pools that remained four to
five feet deep through the past project year. In times of heavy rains the valley
becomes a torrent. The water may rise 30 feet in a few hours. No arroyos containing
water, except immediately after rains, enter the river except near the town of Henrietta
where a creek, which also serves as the effluent of the city sewage-treatment plant,
enter the river.
Between the town of Henrietta and the mouth of the river, the river changes. It
becomes broader and slower, sometimes with scarcely perceptible current. The valley is
broader and banks low and middy. The river bed is of soft silt and mud. At the mouth
of the river, the currents of the Red River have built a bar of relatively firm sand in
marked contrast to the muddy bottom of the Little Wichita. In these last few miles of
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h,
the river's length, water is permanent although, when flowage ceases upstream, there
is no current and water analyses indicate that waters of the Red River may actually
back into the lower part of the Little Wichita River. The fish population of this part
of the Little Wichita River is also derived directly from the Red River.
DESCRIPTION OFSAMPLE STATIONS
FULDA STATION. - This station is located on the headwaters of the Little
pss River, directly south of the Railroad Station of Fulda in Baylor County. ‘The
ver is intermittent. In times of high water, but not flood, a moderate current is pre-
sent in water four to five feet deep in a narrow and vertical-banked channel. Usually
the river consists only of a series of unconnected pools from four to five feet deep,
at deepest, separated by a few to a hundred yards of firm sand and gravel. When several
weeks have passed without rains, the smaller pools dry up, but even at extreme drought
during the project period, some water was found in the largest and deepest pools. The
river banks are packed gravel overlaid by floodplain silt. Broad-leafed trees, briars
and rather dense vegetation form a narrow belt along the river. Water quality is good.
Turbidity is quite high, even in the still pools in the river bed. Fish, almost all
of small size, are numerous in the pools in the river bed where concentrated by receding
water. Fish collections were obtained by seining.
KICKAPOO STATION. - Of the stations on the upper parts of the river, Kickapoo
Station alone supports large fishes. The station is located where the river enters
Lale Kickapoo, and during the course of the project year, Lake Kickapoo was at a
relatively high to very high level. The station is located in front of a rocky bluff
which turns the river and forms a constriction that may be considered the point where
the river ends and lake begins. The land on the side of the river opposite the bluff
is low, flat and muddy, overgrown with drowned salt-cedar brush. Ordinarily the river
is placid here, with scarcely perceptible current. After rains the current is strong
and large trees and stumps are carried downstream, to remain along the shore as drift-
wood or to sink in the calmer waters of the lake and form deadheads. The water is
customarily quite turbid and brownish with suspended silt. Fish collections were
obtained with gill nets and by seining.
ARCHER STATION. - On the map a considerable distance separates Archer Station
from Kickapoo Station, but it must be remembered that much of this distance is covered by
Lake Kickapoo (already reported, F7R1, Job B-3) and part of the remainder, below
the Lake Kickapoo dam, is almost always dry. The Station is situated where the bridge
on State Highway 79 crosses the river just north of Archer City. The river is
intermittent at this station but never in our experience is.it dry. Usually there are
pools connected with narrow trickles of running water, and some of the pools are six
feet or more in depth. The river flows in a deep, muddy, "V-shaped" canyon. The
stream bed is gravel and, in deeper places, silt. Vegetation is rather dense and a
broad band of wooded land fringes the river. Water is usually turbid but sometimes
rather clear, especially in winter. Fishes are small. Collections were made with
seines or, when conditions were optimal, rotenone.
SCOTLAND STATION. = Scotland Station is located in Archer County just north
of the town of Scotland, where the river is crossed by the bridge on Highway U. S. 281.
Conditions are in most respects very similar to those at Archer Station, principal
difference being the deeper valley and presence of salt water pollution sites in the
vicinity.. Fish collections were usually taken by seining but on a few oceasions by
the use of rotenone.
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5.
HENRIETTA. = Conditions at Henrietta Station are distinctly more humid than
farther upstream. The station is located just west of the town of Henrietta, in Clay
County, where the river is crossed by the bridge on Highway U. S. 82-287. The valley
is "V-shaped" but not as deep as at Scotland Station, nor-is it as broad. Usually
there is a current here, but on several occasions the river consisted of only a series of
disconnected pools in the river bed. The bottom was uniformly middy, gravel occurring
only in riffles, and the water turbid and brownish with silt. Most fish collections
were taken with seines but some rather complete collections were obtained with the use
of rotenone.
Henrietta Creek, the sewage effluent of the town of Henrietta, enters the river a
few miles downstream from Henrietta Station. The creek was checked. The sewage is
treated and the water quality of the effluent is good. The creek is broad and sluggish.
European carp and gizzard shad were noted in the creek but a complete collection was
not made.
RIVERMOUTH STATION. - This station is located just above the point where the
Little Wichita River enters the Red River. Gill nets were set in the stiller waters
upstream from the sand bar that marks junction of the two rivers but seining was confined
to the bar itself. The river is broad and still here, with a bottom of mud so soft and
deep that we found it impossible to seine. Streamside vegetation includes dense growths
of willows and salt cedars . The more swiftly flowing Red River has built a sandbar at
the mouth of the Little Wichita, and waters of the Red Riverswirl into and contaminate
the non-saline waters of the Texas stream. The high quantity of dissolved solids of
the Red River change the water quality of the mouth of the Little Wichita enormously,
decrease its turbidity, and the fishes present are typical of the Red River rather than
the Little Wichita River.
Table 1. Volume of Water in the Little Wichita River at Archer Station.
Period . Mean Discharge (cubic ft./sec.) Total Runoff (acre feet)
Average annual, 1932~55 82.6 59800
for year 1955 88.4 63980
January, 1955 Tel3 . 438
February, 1955 17.0 943
March, 1955 9.85 606
April, 1955 2h 1 1430
May, 1955 83.5 9130
June, 1955 110.0 6570
July, 1955 2.54 156
August, 1955 .26 16
September, 1955 512.0 30460
October, 1955 297.0 18230
November, 1955 dry -=
December, 1955 ary --
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6.
Table 2. Physical Conditions at the Sample Stations.
ne
Date Air Temp. Water Temp. Turbidity (mm. ) pH
scaring egiiantbemutptbmielein dbase tim belch limita shill i
FULDA STATION
7/12/55 - - - 7-85
8/22/55 - - - 7-73
9/9/55 39 29 ~ 190 -
10/23/55 33 28 165 7.6
11/8/55 21 10 145 7.3
12/13/55 9 8 300 plus 8.25
1/10/56 6 5 275 7.65
2/16/56 9 8 180 7.35
3/1/56 21 16 260 7.85
4/6/56 25 21 75
5/6/56 36 27 30
KICKAPOO STATION
7/26/55 33 29 100 7+70
8/23/55 30 29 105 7.94
9/15/55 26 27 140 -
10/9/55 23 22 160 Tot
10/16/55 19 20 90 7.8
11/12/55 14 12 2h5 7.6
12/5/55 2 9 290 8.18
2/21/56 L7 11 100 8.03
4/5/56 22 20 155 8.0
5/15/56 23 22 80 -
ARCHER STATION
7/11/55 - - - 7-70
7/28/55 - - - 7.65
8/23/55 - . - 1.55
9/8/55 39 27 110 -
10/13/55 28 21 70 TE
11/9/55 1g 10 90 7.6
12/23/55 6 T 230 7.60
1/20/56 6) 4 120 7.75
2/5/56 8 5 150 8.15
3/8/56 27 16 340 7.65
4/15/56 19 it 185 -
5/8/56 37 30 ho -
SCOTLAND STATION
7/11/55 - - ~ 7.95
7/28/55 - - - 7-60
8/23/55 - - - 7-50
9/8/55 33 2k 195 -
10/13/55 29 22 85 7.5
11/1/39 18 12 750 7.6
12/24/55 16 k 775 7.84
1/22/56 1 4 100 7.72
2/9/56 8 6 110 8.0
3/5/56 26 16 350 7.70
4/12/56 2h 20 210 -
5/9/56 38 29 65
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Table 2. (Continued)
Date Air Temp. Water Temp, Turbidity (mm. ) pH
HENRIETTA STATION
Aw -
wi
7/11/55 - - = 8.
7/28/55 - - - t
8/23/55 - - : ie
9/9/55 31 28 75 _
10/13/55 2k 22 65 TF
11/24/55 16 13 70 7.5
12/26/55 6 h 725 7.45
1/12/56 5 4 70
2/4/56 15 9 _ 220 7-75
3/4/56 18 12 280 7.78
4/11/56 21 19 160 _
5/12/56 36 29 65
RIVERMOUTH STATION
7/12/55 - . - 7.50
7/27/55 25 28 1k5 TAS
8/23/55 27 29 260 7.28
9/7/55 28 28 260 7:55
10/19/55 31 18 105 TA
11/23/55 6 13 400 T+5
12/9/55 10 6 600 7.82
1/13/56 11 5 195 7-70
2/16/56 11 9 4O5 7.20
3/30/56 ak 20 250 .
4/18/56 15 16 200
5/13/56 28 oh 35
5/17/56 32 23 75
All temperatures are Centigrade. Turbidity is Seichi disk readings in millimeters.
pH was determined with a Beckman pH meter.
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8.
Table 3. Chemical Nature of the Water at the Sample Stations.
Date Calcium Sodium Chloride Sulfate Carbonates Total Salts
FULDA STATION
7/12/55 36 14 22 - 134 206
8/22/55 36 2 4 - 128 170
9/9/55 38 22 33 - 145 238
10/22/55 34 6 9 31 6). 1h)
11/10/55 48 T 11 20 122 208
12/10/55 56 6 9 6 165 2h1
1/10/56 48 ho 34 fe) 165 287
2/16/56 86 118 195 ) 213 612
3/1/56 64 10 8 20h Lv? 469
4/29/56 116 18 17 30 336 517
5/6/56 iby 9 12 20 113 198
KICKAPOO STATION
7/26/55 yy 21 12 - 162 239
8/22/55 56 12 18 - 168 254
9/24/55 dy i 7 - 162 234
10/9/55 38 18 29 ~ 125 210
10/16/55 28 16 9 - 110 153
11/12/55 38 8 12 - 137 195
12/4/55 56 9 14 2h 137 2h0
12/29/55 66 12 18 63 135 293
2/20/56 Lo 21 14 fo) 149 224,
3/24/56 yh 21 10 12 148 235
h/4./56 50 23 20 Ly 149 259
5/14/56 46 13 12 35 127 238
ARCHER STATION
7/11/55 54. 84. 131 ~ 202 471
7/28/55 52 122 188 22 119 503
8/23/55 hg 19 31 - 181 279
9/8/55 4h 26 ho - 216 326
10/13/55 38 12 18 = 128 196
11/9/55 he 12 18 . 2h6 318
12/22/55 100 66 101 58 232 557
1/20/56 58 ke 33 ) 170 303
2/9/56 72 62 85 31 198 148
3/4/56 190 319 763 - 110 1382
4/21/56 332 183 1159 110 162 2246
5/8/56 5h ke 67 ho 109 312
SCOTLAND STATION
7/11/55 50 aa 67 - 170 331
7/28/55 56 1k9 231 39 116 591
8/23/55 he 76 119 149 386
9/8/55 132 456 700 192 156 1637
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Table 3. (Continued).
Date
10/13/55
11/9/55
12/24/55
1/22/56
2/5/56
3/5/56
4/11/56
5/9/56
7/11/55
7/28/55
8/23/55
9/9/55
10/13/55
11/24/55
12/26/55
1/12/56
2/16/59
at
5/12/56
7/12/55
7/28/55
8/23/55
9/7/55
10/19/55
11/23/55
12/8/55
1/12/56
2/15/56
3/30/56
4/18/56
5/13/56
5/17/56
Calcium
252
58
162
ehh
64
360
ok
3h2
392
29h
530
46
36
16
50k
910
38
28
Sulfate
Th
121
)
©)
aly
35
HENRIETTA STATION
39
181
238
h
ah
67
66
29
78
59
Th
61
ho
ah
38
ok
ho
RIVERMOUTH STATION
793
131
612
905
ik
1199
1190
543
1566
1690
1591
57
kL
92
60
303
475
101
686
830
296
902
705
876
27
ah
Carbonates
131
167
198
146
180
122
153
104
132
92
97
122
68
226
238
345
143
198
183
110
83
Total Salts
210
754
1000
258
236
47h
635
122
205
12
430
309
4O7
357
521
368
2179
426
1570
2332
251
3453
2056
4053
4160
278
212
Dashes indicate insignificant amounts, not checked to exact amounts but less than
5 ppm. Carbonates are almost entirely bicarbonates at prevailing pH, and include
carbon dioxide also. Total salts are totals of those listed.
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10.
QUALITY OF WATER OF THE LITTLE WICHITA RIVER
Before the water analyses listed in Tables II and III can be interpreted, certain
considerations must be taken into account. Water samples were taken in pools in the
intermittent parts of the river. In dry periods the water in the pools evaporated,
concentrating the solids. In these same parts of the river a rain, even a local
thundershower, is sufficient to dilute these solids greatly. The wide fluctuations
in the readings at Fulda Station in Table III are the result of such concentration and
dilution. On the other hand, the river is constant and deep at Kickapoo Station, and
the variation there is slight.
There are oil wells with surface salt pits in the vicinity of Archer and Scotland
Stations. Here, in periods of dry weather, sodium chloride escapes to the river in
underground flow and, when concentrated by evaporation in pools in the river bed, gives
extremely high readings for sodium and especially for chloride. Here, too, dilution
by rainwater is swift and enough precipitation to wash the salts as far as Henrietta
Station also dilutes them. Because there is more water in the river at Henrietta Station,
under ordinary conditions, the variations in the chemical nature of the water is less
there «
At Rivermouth Station, water from the Red River backs into the Little Wichita
River in times when the Little Wichita is low. Thus the mouth of the Little Wichita
River often contains water adulterated with Red River water, and this accounts for
the high salinities sometimes encountered there. However, in times of rain the Little
Wichita River rises rapidly, flushing out the Red River water and often flowing remark-
ably pure.
When these factors are understood, the water of the Little Wichita River may be
described as: “of good quality, mildly alkaline, quite turbid, and low in dissolved
salts other than carbonates." If the oil-well brine pollution now existing is stopped,
the waters of the proposed lake or lakes should be very similar to the water of Lake
Kickapoo.
ANNOTATED CHECKLIST OF SPECIES OF FISHES OF THE LITTLE WICHITA RIVER
Lepisosteus osseus. Longnosed Gar. This species is quite common near the mouth
} the river, where the bulk of our specimens were taken, but we found it uncommon at
Kickapoo Station. None was taken at any of the other stations. The longnosed gar does
sometimes enter small streams and it is surprising that we found it only in deeper
waters. Near the mouth of the river this fish is sometimes a pest, stealing bait from
fishermen's lines and rarely becoming captured.
Lepisosteus platostomus. Shortnosed Gar. Strangely enough, we took no shortnosed
gars at Rivermouth Station, where longnosed gars were common. The species was uncommon,
although the most mumerous gar, at Kickapoo Station. None was taken at the other stations.
Scaphirhynchus platorynchus. Shovelnosed Sturgeon. We know of but a single
sturgeon taken in the Little Wichita River. This was caught by a fisherman near the
river mouth in 1953, and preserved for some time in the local high school.
Dorosoma cepedianum. Gizzard Shad. This fish was recorded at all stations but
was taken regularly only at Kickapoo Station and Rivermouth Station, where the water
was deep. Only small numbers of immature specimens were taken elsewhere. At the deeper-
water stations, the shad is one of the most abundant fishes. Shad from the river average
somewhat smaller than those from impoundments. The largest specimens caught weighed
scarcely two pounds.
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li.
Hiodon alosoides. - Goldeye. The goldeye is a species that ranges from the Red
River northward, entering only the northern fringe of the State of Texas. It is known
to enter the Big Wichita River for many miles (Completion Report, F7R2, Jobs A-2 and
6-B,) but in the Little Wichita River it is rarely found more than a mile or so from the
Red River. There the species is one of the most common fishes. Specimens taken are
remarkably similar in size, averaging about one pound in weight.
Ictiobus bubalus. - Smallmouth Buffalo. This buffalo is a large fish and in
the Little Wichita River we found it only in the deep-water stations, Kickapoo and
Rivermouth. It is not very common in the river but is of regular occurrence where found.
The largest specimens taken weighed between four and five pounds.
Ictiobus cyprinellus. Largemouth Buffalo. As elsewhere in Northern Texas, the
largemouth buffalo is less successful than the smallmouth buffalo in the Little Wichita
River. Our few specimens were taken at Rivermouth Station and Kickapoo Station.
Carpiodes carpio. - River Carpsucker. The carpsucker is one of the most successful
species of large fishes to occur in Northcentral Texas. It is as widespread and abund-
ant in the Little Wichita River as elsewhere. Specimens were taken at all stations,
but most were young individuals, less than a foot in length, except at the deep-water
stations, Kickapoo and Rivermouth. At these latter stations the carpsuckers averaged as
large and plump as those in the impoundment lakes.
Cyprinus carpio. - European Carp. The distribution of the carp in the Little
Wichita River is unlike the distribution of the buffalos and carpsuckers which super-
ficially resemble it. We found no carp at Funda Station, though this may have been
due to chance. Carp were also more common at the deepwater Stations, Kickapoo and
Rivermouth, than elsewhere but were only moderately numerous there. However, mature
carp are of regular occurrence along the entire river, and large individuals were taken
at Archer Station, Scotland Station, and Henrietta Station. Enough carp of large size
were seen elsewhere along the river to show that they are uniformly distributed. Mature
carpsuckers and buffalos are rarely found away from the deep water stations. Small
carp were taken at all stations except Fulda Station.
Hybopsis storeriana. = Silvery Dace. This form seems to be rare in the upper
reaches of the Red River. We found but a single specimen in the Big Wichita River,
and took two, both in the same seine drag, at the mouth of the Little Wichita River.
Hybopsis aestivalis. - Speckled Dace. Although common in the Big Wichita River,
the speckled dace is rare in the Little Wichita River. We found it of regular occurrence
at Rivermouth Station, but took it nowhere else in the river. In our experience this
dace prefers saline waters, relatively clear water, and a sand or gravel bottom where
the current is moderately swift. Such conditions are absent in the Little Wichita River
except near the river's mouth.
Notemigoneus crysoleucas. - Golden Shiner. We would have guessed that the Little
Wichita River, with its many deep, still pools, turbid, warm water, free of appreciable
salts, would constitute ideal conditions for this species. Nevertheless, it is rare in
the river. We took it twice at Fulda Station and once at Scotland Station, but nowhere
else.
Pimephales promelas. - Fathead Minnow. The fathead minnow is a “pool” fish,
preferring quiet backwaters. Conditions for it are optimal in the Little Wichita River.
--- Page 12 ---
12.
As a result it is widespread in the river, being taken at every station except River-~
mouth Station (where conditions are not optimal,) but it is not as abundant as we
would have expected. It appears from our records that the fathead is relatively less
common in winter than at other times of the year.
Pimephales vigilax. - Parrot Minnow. The parrot minnow prefers waters almost
opposite from its relative, the fathead minnow. Clear, swift water with sand bottom
and riffles are its habitat. The only part of the Little Wichita River suitable for
the species is Rivermouth Station, where it was found on several occasions. Elswhere
in the river its occurrence is sporadic and unpredictable.
Hybognathus nuchalis. - Silvery Plains Minnow. This is a fish of clear, saline
swift waters. Conditions in the Little Wichita River are not suitable for it, except
at Rivermouth Station where it is abundant. The few scattered records from farther
upstream are probably released fishermen's bait. The species is the preferred bait
minnow of the region and countless thousands are sold yearly for bait.
In earlier reports this minnow was listed as Hybognathus placita. Proof that
the Texas form of the plains minnow is conspecific with the northerm H. muchalis re-
quires reduction of the name placita to subspecific rank under the species name nuchalis.
Phenacobius mirabilis - Suckermouth Minnow. We took but a single suckermouth
minnow in the Little Wichita River, at Rivermouth Station. It was undoubtedly a stray
from the Red River. Apparently the species does not like the turbid, non-saline waters
of the Little Wichita River.
Notropis bairdi. - Baird Shiner. This saline-water shiner is found in the Little
Wichita River only at the mouth of the Red River. There it is of regular occurrence
except during the winter months.
Notropis buchanani. - Ghost Shiner. Our records of this species are rather
erratic. One month large numbers may be taken at a station, and the next month none
are taken at the same station. We feel that this is the result of the schooling
habits of this species. If the seine envelops a school of these small fishes, a large
collection is obtained. On another occasion the seine may miss the schools, even
though the species is abundant in a pool. We took the ghost shiner at every station
and sometimes it was the most common shiner in a collection.
Notropis lutrensis. - Red Shiner. The red shiner is ubiquitous. We took it at
every station on almost every occasion when a collection was made, and usually it was
the commonest forage fish present.
Notropis percobromus. - Plains Shiner. Like the Baird shiner, this is a species
of clear, saline, swiftwaters. It was of fairly regular occurrence in the saline
waters at Rivermouth Station but was not found farther upstream. It may be considered
a Red River form straying regularly into the mouth of the Little Wichita River.
Notropis potteri. - Broadhead Shiner. This is another saline-water species.
Usually the broadhead shiner and the Baird shiner are found together in Northcentral
Texas, with the broadhead shiner much less common than the Baird shiner. This same
relationship is maintained at Rivermouth Station in the Little Wichita River. The
species was not found elsewhere in the river.
--- Page 13 ---
13%
Pilodictus olivaris. - Flathead Catfish. The flathead is said to be fairly common
in deeper pools in the Little Wichita River, and many are caught by illegal "grappling."
We found the species uncommon, taking one at Henrietta Station and three at Kickapoo
Station. We took several fingerlings of this species at Henrietta Station, in addition
to those listed above. The species spawns in the river.
ictalurus punctatus. - Spotted Channel Catfish. A number of channel catfish of
fair size were taken in the deep-water stations, Rivermouth and Kickapoo. Numerous
specimens of small size were taken at the other stations. The species seems to be of
general distribution in the river.
Ameiurus melas. Black Bullhead. The black bullhead is of general distribution
in the Little Wichita River except in the lower reaches. We took none at Henrietta
Station, but suspect that this was the result of chance. At least we see no reason
why black bullheads should not occur there. None was taken at Rivermouth Station, but
we would not expect them to occur in the saline water present there.
It has recently been proposed that the bullheads now placed in the genus Ameiurus
be shifted to the genus Ictalurus. Pending further clarification and acceptance of
this proposal, which we feel sure will be resisted, we prefer to retain tle current
generic usage.
Ameiurus natalis. ~ Yellow Bullhead. We were greatly surprised to find the
yellow bullhead in the Little Wichita River, because it is absent from tle Big Wichita
River and, apparently, from other streams in Northcentral Texas. Apparently, the
species is extremely susceptible to high salinity. We took many specimens at Fulda
Station, above Lake Kickapoo, and three others at Scotland Station when rotenone was
used to kill all the fishes in a deep pool.
Schilbeodes mollis. - Tadpole Madtom. This is another species we were surprised
to find in the Little Wichita River, because we have found it nowhere else in North-~
central Texas. Apparently the species does not occur in saline waters. Madtoms were
taken at Archer Station, Scotland Station, and Henrietta Station. We found none at
Kickapoo Station but seining in the deep water there is so difficult that the species
might have been overlooked. None were taken at Fulda Station, however, where seining
was so thorough that, had madtoms been present, they would have most certainly been
captured. The absence of the species in the saline waters at Rivermotth Station is
to be expected.
Because the madtoms of the Little Wichita River seem to be isolated by saline
waters, we wondered if they might not have envolved a distinct race there. We therefore
sent specimens to Dr. Frank Cross, at the University of Kansas. Dr. Cross considered
the specimens typical of S. mollis.
Gambusia affinis. - Mosquitofish. Mosquitofishes are almost as widespread and
abundant as red shiners. Specimens were taken at every station and in most seine
hauls, Because mosquitofishes are surface-shoreline haunters, it is difficult to
obtain them in numbers comparably representative of the other fish species present in
an area. Those taken were usually caught when the seine was brought in to the bank.
Had special effort been made, thousands could have been captured in some seine drags.
We feel that by counting only specimens taken in normal seining operations, without
extending the seine~drag along the shoreline unduly, fairly representative samples
were obtained.
--- Page 14 ---
14.
Morone chrysops.- White Bass. Locally called “sand bass," the white bass is a
favored game species. The muddy bottom and turbid waters of most parts of the Little
Wichita River are unsuited to this species, and all of our records were obtained at
the deep-water stations, Kickapoo Station and Rivermouth Station. It was of rather
regular occurrence at both stations.
Micropterus salmoides. =- Largemouth Black Bass. We took a small bass at Scotland
Station, a large individual at Rivermouth Station, and six others at Kickapoo Station.
Apparently the species is uncommon in the Little Wichita River, possibly because of
the extreme turbidity of the water. Some of the fish taken, however, were of good size
and the scattered records show that the river is capable of supporting bass for all of
its length.
Lepomis cyanellus - Green Sunfish. An abundant species, taken at every station
except Rivermouth Station, where only a single sunfish was taken in the course of the
study. Seining conditions on the sandbar at this station are such that sunfishes
usually escaped capture. Doubtless, green sunfishes were abundant at this station
as elsewhere.
Lepomis humilis. ~ Orangespot Sunfish. Throughout most of the river, this sunfish
was widespread but uncommon. None were taken at Rivermouth Station. Through the year,
however, an increase in numbers of this species was noted at Fulda Station. In April
and May the river receded to a series of pools in the river bed and some of these pools
contained hundreds of orangespot sunfishes in breeding coloration - a most colorful
sight.
Lepomis macrochirus. ~ Bluegill Sunfish. Bluegills were taken in small numbers
at every station except Rivermouth Station. The species is not as common as some of
the other kinds of sunfishes in the river. No large fishes of this species were found
in the river.
Lepomis megalotis. ~- Lengear Sunfish. The longear sunfish was almost as abundant
sh.
as the green sunfi Specimens were taken at every station and are represented in
most collections. The only sunfish taken at Rivermouth Station was a longear.
Chaenobryttus coronarius. Warmouth. Warm water, muddy bottom, and turbid, still
pools are typical habitat of this fish. We would have expected it to be common in the
Little Wichita River but we found it only once, when two specimens were taken in a
seine haul at Scotland Station.
Pomoxis annularis. ~ White Crappie. Crappie were taken at every station, always
in the deeper pools. In the deeper water at Kickapoo Station and Rivermouth Station,
the crappie is one of the most numerous of the larger fishes.
Percina caprodes. =- Logperch. The logperch is present in Lake Kickapoo, but seem
to be quite scarce in the Little Wichita River. Our only records are two specimens
taken at Kickapoo Station.
It has recently been proposed that the genus Percina be placed in the synonomy
of Hadropterus, on the grounds, in part, that the generic character, long snout, is
missing in specimens from various localities. We are heartily in accord with this
treatment, but prefer to wait for more general acceptance of the change before accept-~
ing it. Logperches from both the Big Wichita River drainage and the Little Wichita
--- Page 15 ---
15%
River drainage have short snouts, and form 4 local race, possibly worthy of taxonomic
recognition at some future time.
Aplodinotus grunniens. ~ Freshwater Drum. The drum seems to be quite uncommon
throughout the length of the Little Wichita River. We took several specimens when
pools in the riverbed at Fulda Station were treated with rotenone, but elsewhere we
took only one or a few individuals.
--- Page 16 ---
16.
Table 4. Total Numbers of Fish taken at the Little Wichita River Stations.
Species Fulda Kickapoo Archer Scotland Henrietta Rivermouth
. osseus - 3 - - = 83
» platostomus = 17 = - ~ 2
Scaphi rhynchus = - - - - =
Dorosoma 677 3 13 20 235
Hiodon - - - - - Li2
I. bubalus - 2h - - - ak
I. ¢yprinellus = 7 - - - h
‘ariekea 1 90 4 19 2 253
Cyprinus - kg 6 15 2 20
H. storeriana = - - - ~ 2
H. aestivalis - - - - = 10
Notemi goneus 3 = - aL. - =
P. promelas 12 72 31 168 45 -
P. vigilax 11 6 21 3 3 64
Hybognathus - 2 - 3 - 7416
Phenacobius = - - - - ih
N. bairdi - - - - - 53
N. buchanani - 27 10 111 591 186
N. lutrensis 281 108 228 570 222 415
N. percobromus - - - - - 160
N. potteri - - . - . 16
Pilodictus * k = 2 1
Ietalurus 26 26 14 23 5 11
A. natalis 34 - - 3 - ~-
A. melas 3 50 79 138 - -
Schilbeodes = = 12 3 25 1
Gambusia 159 179 519 120 209 20
Morone - 19 ~ = - 55
Micropterus = 9 = 2 = 1
L. ¢cyanellus 32 11 39 74 47 -
L. humilis 626 7 8 13 29 -
Le macrochirus 56 2h 1 - 6 -
L. megalotis 126 57 37 43 62 1
Chaenobryttus ~ = ~ 2 - -
Pomoxis 3 187 8 9 13 27
Pereina - 2 ~ ~ ~ -
Aplodinotus 12 2 1 1 5 7
Note; Included here are all fishes taken, including immature specimens of larger species,
taken in seine drags.
--- Page 17 ---
17.
Table 5. Monthly Variation in Species and Numbers of Forage Fishes.
en
FULDA STATION
7/10 8/23 9/9 10/23 11/8 12/13 1/10 2/16 3/1 4/6 5/6
Notemigoneus = ~ ~ - = - = - ue a -
P. promelas 4 - 3 a - - “ a 3 i. ”
P. vigilax - - ll - - - - - = = =
N._lutrensis - ke 26 13 9 a3. 22 7 «37 «+101 13
Gambusia_ - 19 6 - 9 17 65 31 i 5 Oe
L. cyanellus 2 17 - - = - “8 - -
L. humilis 5 9 16 - ~ 3 ~ 21 66 499 7
L. macrochirus - - - « ~ - - - 1 = «64SlClCtie
L. megalotis - 14 ~- 2 -* = 1 - 5 100 1
KICKAPOO STATION
8/23 9/24 10/9 10/16 11/12 12/5 2/21 &/hk 5/16
72
6
2
18
21
promelas
° vigilax
bo thus
buchannani
- lutrensis
ambusia
cyanellus
humilis
macrochirus
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ercina
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ARCHER STATION
7/28 8/23 9/8 10/13 11/9 12/23 1/20 2/5 3/8 4/15 5/8
t 6 9
= 21
9
T
- ii
1.
16
6
22
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N. lutrensis
Schilbeodes
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L. cyanellus
L. humilis
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--- Page 18 ---
18,
Table 5. (Continued).
SCOTLAND STATION
7/28 8/23 9/8 10/13 11/7 12/24 1/22 2/9 3/5 4/le 5/9
Notemigoneus = = - = = = ~ 1 ~ in ia
P. promelas 9 25 132 «(- - 2 as 9 i a *
P. vigilax - - 3. - = ~ - - - s i
Hybognathus - - - = 2 al - ~ ~ = =
N. buchanani . . ~ - - - 41 2 60 - 8
N. lutrensis k7 11g 6 22 7 310 16 22 9 i. 2
Schilbeodes = = 3 - - ~ - - ~ az ti
Gambusia 28 33 23 - - - - 36 =O = ™ -
L. ¢yanellus 6 46 14 - - we 1 1 ‘ 7 “a
L. humilis 2 2 8 ss i = - = if uy -
L. megalotis 3 T 20 7 = = 2 = 3 a 1
Chaenobryttus 2 = - - ~ = a és wa we ‘ii
HENRIETTA STATION
7/28 8/23 9/9 10/13 11/23 12/26 1/12 2/h 3/h 4/1 5/12
P. promelas - y 9 = - - - 16 - 2 12
P. vigilax - 2 1 - 1 - - - ~ . i,
N. buchanani i. 220° 33 ~ @3, 2-15 16 46 - 106 71
N. lutrensis 90 1k 12 26 4, 2 30 2 15 21 9
Schilbeodes - - 19 - 6 - - - = - 1
Gambusia 9 16 16 “ 12h ky ™ ~ “ ~
L. cyanellus 5 2 8 - 2. #1 - x 86 7 -
L. humilis 2 2 6 = 15 “ “ 3 - 7 -
L. macrochirus - “ = = ~ = - 1 3 2 i
L. megalotis 16 1 - - 4300Ce - 2 -= : ae
RIVERMOUTH STATION
7/12 8/22 9/7 lo/i9 11/22 12/9 1/12 2/16 3/28 4/17 5/17
H. storeriana - - 2 - ~ w ss si ‘é " i
EH. sestivalis = 3 2 = iu ~ ra a ai 5 =
P. vigilax - - - - - - 56 3 3 =
Hybognathus - 3000 3000 113 121 1010 80 60 6 20 6
Phenacobius ~ = = = - af x - - ~ =
N. bairdi ~ 9 32 7 - - - 4 - i -
N. buchanani - 4e - - dt: . @2 64s ig 32 9
N. lutrensis 22 108 8 3 32: - 15 98 ll il =416 11
N. percobromus - 9 17 ko 26 “ - 23 31 - 14
N. potteri = 2 6 T - - = = a me
Schilbeodes = = = - = 1 i = Pa i si
Gambusia 11 4 4 - 1 - - = - = <i
--- Page 19 ---
19.
Table 6. Percentage Composition and Sex Ratios of Larger Fishes from the Little Wichita
River.
Species Number taken % of total % males % females
Lepisosteus osseus 80 S.7 80 20
Lepisosteus platostomus 19 1.4 67 33
Dorosoma cepedianum 305 22.0 35 65
Hiodon alosoides 172 12.6 50 50
Tetiobus bubalus 4 3.5 75 25
Ictiobus cyprinellus 43. 0 73 28
Carpiodes carpio 353 25.3 55 ks
Cyprinus carpio 73 5.3 50 50
Ictalurus punctatus 38 2.8 37 63
Ameiurus melas 38 2.8 70 30
Pilodictus olivaris \ 3 - 100
Morone chrysops Th 5.3 64 36
Micropterus salmoides 11 8 27 73
Pomoxis annularis 138 10.1 43 57
Aplodinotus grunniens 8 6 25 75
1306 100.3
Note: Not included here or in the following table are the following young, small specimens
taken in seine drags and counted by not weighed and measured: 6 Lepisosteus osseus, 647
Dorosoma cepedianum, 16 Carpiodes carpio. 17 Cyprinus carpio, 234 Ameiurus melas, 37
Ameiurus natalis, 5 Pilodictus Olivaris, 67 Ictalurus punctatus, 1 Micropterus salmoides,
79 Pomoxis annularis, 20 Aplodinotus grunniens.
Table 7. Percentage Composition by Weight and Mean Weights of Larger Fishes from the
Little Wichita River.
Species Weight Taken % of Total Weight Mean Weight
Lepisosteus osseus 122 lbs. T9 1.5 lb.
Lepisosteus platostomus 37.8 2.5 1.1
Derosoma cepedianum 208.8 13.6 “7
Hiodon alosoides 112.2 7.3 wl
Ictiobus bubalus 1h2.2 9.3 3.0
Ictiobus cyprinellus ks 9 3.0 h.2
Carpiodes carpio 455.6 29.6 1.6
Cyprinus carpio 1h0.3 9.2 1.9
ictalurus punctatus 50.2 3.3 1.3
Ameiurus melas 7.9 5 2
Pilodictus olivaris 18.1 1.2 45
Morone chrysops 67.2 ky 9
Micropterus salmoides 37.2 2.4 3.4
Pomoxis annularis 80.0 5.2 26
Aplodinotus grunniens 6.0 a 8
--- Page 20 ---
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