TPWD 1956 F-7-R-4 #201: Basic Survey and Inventory of Species Present, as well as Their Distribution in the Pease River, its Tributaries and Watershed within Wilbarger, Foard, Cottle, Motley,
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JOB COMPLETION REPORT
State of TEXAS
Project No. F7R4 Name; Fisheries Investigations and Surveys of the Waters of
Region 1-B.
Job No. B-10 Title: Basic Survey and Inventory of Species Present, as well
as Their Distribution in the Pease River, its Tributaries
and Watershed within Wilbarger, Foard, Cottle, Motley,
Floyd, and Brisco Counties, Texas.
Period Covered: June 1, 1956 through May 31, 1957
ABSTRACT
Fifty-two seine collections produced a total of 20,005 specimens for study.
Twenty-four species, representing 7 families of freshwater fish were found to occur.
Except in a few isolated holes near the river mouth, the Pease River is valueless for
game fish at the present time. For the most part, the water is excessively salty,
and the river bed is often dry and too shallow to maintain a game fish population.
The fish population is comprised mostly of salt tolerant cyprinids and game wardens
report extensive seining for these species by commercial bait dealers. Since the
water is not suitable for municipal or irrigation purposes, the construction of an
impoundment on the Pease River in the foreseeable future, for any purpose other than
flood control, is unlikely.
ACKNOWLEDGMENTS
Dr. Walter Dalquest, whose employment with the Texas Game and Fish Commission
terminated in October 1956, set up the original stations, conducted all of the labora-
tory work and most of the field work on this job for the first five months. Since
that time, Dr. Dalquest has helped with some phases of work conducted in Region 1-B
and has checked the manuscript of this report. Grateful acknowledgment is also express-
ed to Dr. Carl Gray, Soils Scientist of Midwestern University and Wichita County Water
Improvement Districts, for making the numerous water analyses during this study. Data
on water volume were obtained from Mr. John Joernes, United States Geological Survey,
Water Resources Branch, Wichita Falls.
TECHNIQUES
Sample stations were established at six points along the length of the Pease
River. Eleven collections, approximately one month apart, were made at each sample
station during the study. At each station, chemical and physical data concerning
the water were taken, and seine samples of the fishes present were preserved in for-
malin for laboratory examination and identifications. Since an adequate picture of the
fish population at all points along the river could be determined by seining, no gill
nets or fish toxicants were used. There are no important permanent-flowing tributaries
of the Pease. Water was present at only one tributary during the study, and basic
survey collections were taken from this station in addition to those on the river. On
several occasions, data could not be obtained from some of the station either because
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the river was dry, or because the river was flooded and could not be seined.
PHYSICAL CHARACTERISTICS
North Pease River originates in northwestern Motley County and flows
northeastwardly to just above the Motley-Hall County line, then continues south-
eastwardly across northern Cottle County to its confluence with South and Middle
Pease Rivers. Both the South and Middle Pease Rivers originate in western Motley
County, flow northeastwardly to their convergence in east-central Cottle County,
and continue to their confluence with North Pease River in northeastern Cottle
County. After leaving Cottle County, the Pease River flows southeastwardly across
the southwestern corner of Hardeman County, serves as a boundary line between south~
eastern Hardeman and northeastern Foard Counties, and continues across the northem
section of Wilbarger County to its confluence with Red River.
Headwater streams of the Pease River lie in Permian clays and sandstones,
with abundant veins and stringers of crystaline gypsum. The sediments of Permian age
outcropping along the Pease River form the Pease River Group and are considered to
have been deposited in early-middle Permian time. On the north bank of the river at
Lazare Station, and at an elevation nearly 100 feet above the present river level,
are found extensive Pleistocene gravel deposits that are now being worked commercially.
To the south of the river and only a few yards above the present river level occurs
a well-consolidated conglomerate of unknown age. It seems to differ lithologically
from Pleistocene gravels of the valley of the Pease and other northern Texas rivers,
an no fossils of vertebrate animals were found in spite of rather intensive search.
Downstream from Lazare Station, wind blown sands from numerous dunes and
there are bluffs along the river that consist of reddish, sandy soil and contain
remains of modern buffalos and other Recent animals. The Permian rocks form the
river valley but Recent deposits cover the floodplain of the river itself. There are
local deposits of late Pleistocene age, as at Vernon Station, containing remains
of elephants and other mammals. Other deposits of apparently similar age are found
near the river mouth.
The U. S. Geological Survey discontinued its station on the Pease River in
July 1947. Therefore, stream flow and run-off data are not available for the period
of this survey. Data is available for the monthly and annual mean discharge and
the monthly and annual run-off at Quanah Station from January 1924 to July 1947.
(See Tables 1 and 2).
DESCRIPTION OF SAMPLE STATIONS
NORTH FORK STATION. Located on Highway 83 approximately 18 miles south
of Childress, in Cottle County. The river here has cut a relatively narrow valley
in Permian rocks. There is much shale, gypsum and silt. The river bed is braided
sand and quite firm (not quicksand). The river was dry here most of the year, and
collections were taken from isolated pools below cliffs on the north bank.
MATADOR STATION. Located on Highway 70, approximately 12 miles west of
Paducah, at the Motley-Cottle County line. The valley here is narrow and deeply-cut
into Permian rocks. The river bed is braided sand and apparently dry most of the
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time because grass grows well out on the river bed. Many trees grow along the river's
edge, mostly elms and a few cottonwoods. Collections were made from a deep hole
near the bridge, that apparently holds water for long periods of time. This station
is the point farthest up the river that is worthy of maintaining as a station. Since
this station was dry for the first 6 months of the study, it was discontinued in Nov-
ember 1956, and replaced by South Fork Station approximately 25 miles downstream.
SOUTH FORK STATION. Located on Highway 83 about 6 miles south of North Fork
Station and 15 miles north of Paducah. This station is approximately 10 miles below
the confluence of the Middle and South Forks of the Pease River. The river bed is
similar to that of the North Fork, but the valley is narrower. Except during a period
of heavy rain, in May 1957, this station was dry. A tree at least 10 feet high, in
the middle of the river bed, indicates a normally dry condition.
LAZARE STATION. Located about 12 miles south of Kirkland and near the very
small town of Lazare. The confluence of the North and South Forks of the Pease occurs
about 3 miles upstream. Approaching this station from the north, one descends through
a series of cut terraces in Permian sediments. Deposits on the north bank are sand-
stone, shale, gypsum and dolamite. To the south the rise is more gradual, and much
of it is through a gravel and conglomerate series of many yards thickness. This mat-
erial appears entirely non-fossiliferous. The river bed is broad and of braided sand.
Running water was present each time this station was worked.
QUANAH STATION. Located on Highway 283, approximately 15 miles south of
Quanah. This station is in a valley cut into Permian silt, sandstone and dolamitic
limestone. To the north, in the direction of Quanah, the land rises greatly in level
after level of terraces cut into Permian sediments. No Pleistocene and little Recent,
even on highest level. The river bed is quite broad, of braided sand, and rather muddy.
Running water was not always present, but there were several large pools from which a
collection could always be obtained.
WEST VERNON STATION. Located on Highway 287, about 3 miles northwest of
Vernon. The valley is broad and shallow with bluffs of bedded materials, mostly flood-
plain sand, on the north side. The river bed is very wide and braided, with the flood
level approaching one-half mile in width. Bed is sand and quicksand. Very little
streamside vegetation except salt cedar. When the stream was not flowing, there were
deep holes (up to 6 feet in depth) under the bridge from which collections were taken.
VERNON STATION. Quite similar to West Vernon Station and within sight of it.
Located on Highway 203, immediately north of Vernon. This station was discontinued
in January 1957, because it was not different enough from the West Vernon Station. ‘Tt
was set up as a station originally because it was thought to be below the sewage plant,
it was discontinued and a new station (East Vernon) was set up below the effluent ditch.
EAST VERNON STATION. Located about 2 miles east of the city of Vernon and
about one-half mile below the sewage effluent ditch. The river is quite often dry,
except for the water provided by the sewage plant effluent. When the river is flowing,
fish species similar to those of the stations further upstream may be found here.
When the river is not flowing, fish are trapped in stagnant pools of sewage water and
usually die. There are signs of bank fishing farther downstream (probably for carp).
Tracks and other indications of commercial bait seining are evident between this sta-
tion and the mouth of the river.
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SHORES CREEK. Located 3 miles north of North Fork Station on Highway 83.
This creek is in a narrow canyon with steep walls. The creek consists of standing
holes of water 50 to 200 feet long connected by seeping stream flow. Bottom is sandy
and rocky with thin covering of silt. There is no vegetation in.the canyon, and the
walls have jutting rocks heavily laced with stringers of gypsum. Rocks and snags in
the creek bed made seining very difficult. Only Hybognathus and Pimephales promelas
were taken at this station.
Physical data: Air - 72; Water - 57; Turbidity - 500 plus
Chemical data: .. ca. na. cl. ‘sok co3 heo3 Total pH
1054 34 28 2h67 6 1h9 110 8.4
CHEMICAL CHARACTERISTICS OF WATER
The chemical nature of water at the sample. stations is given in Table 3.
Except during periods of rainfall and where it is diluted by sewage effluent from the
city of Vernon, the water in the Pease River is too salty and "gypy" to support most
species of freshwater fishes. The source of these natural polluting salts is probably
springs whose waters have percolated through gypsum and halite beds of Permian age.
POLLUTION
No industrial waste was found to enter the Pease River. The only sewage
effluent entering the river is from the city of Vernon. Water from this effluent was
checked on''séveral otcasions..and was always found. to be well, treated, free of all solids,
and clear. Treated water is carried from the treating plant in an enclosed pipe direc
ly to the effluent ditch, where it falls onto large concrete blocks and flows approx-
imately 400 feet to the river. Frogs, turtles and algae were observed in the ditch.
When water is flowing in the river at this point, it is actually improved by the treat-
ed sewage water. When the river is not flowing and diluting the sewage effluent, it
is quite common to find sick and dead fish (mostly carp, carpsucker, bullhead catfish
and native minnows) in the river and along the banks.
PHYSICAL CHARACTERISTICS
Physical conditions at sample stations are shown in Table 4. For the purpose
of this survey,, turbidity was measured with a secchi disk. Measurements were made in
deepest water found at the station. Frequently, the disk was clearly visible on the
bottom, in which case the turbidity was recorded as the depth of the water "plus".
FISH COLLECTIONS
A total of 24 species, representing 7 families of freshwater fishes was
taken from the Pease River during the segment period. Monthly variations in species
and numbers of fishes taken at each of the sample stations are given in Tables 5
through 11. The total numbers of fishes taken at all of the permanent sample stations
along the river are giver in Table 12.
There were 20,005 specimens collected from the seven permanent sampling
stations.
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Family Clupeidae
Herrings
Dorosoma cepedianum: gizzard shad. We took 66 specimens during the study,
comprising 0.3% of the total.
Family Catostomidae
Suckers
Carpiodes carpio: river carpsucker. Only 117 specimens were taken, all but
one of which were captured near the river mouth, close to Vernon.
Family Cyprinidae
Shiners and Minnows
Cyprinus carpio: carp. Twelve carp were collected, all at West Vernon
Station.
Hybopsis aestivalis: speckled chub. A total of 94 specimens was taken at
4 stations.
Notropis percobromus: plains shiner. Sixteen specimens were taken at West
Vernon and Quanah Stations.
Notropis brazosensis: Brazos River shiner. Only 4 specimens were taken,
all at West Vernon station, in December 1956.
Notropis potteri: chub shiner. Although not numerous (0.39% of the total)
this species was represented at all but 2 stations during the study. It was not taken
at South Fork Station )dry except during floods) or at East Vernon Station where adequ-
ate water was not present to dilute the sewage effluent.
Notropis bairdi: Red River shiner. This, one of the most abundant species
in the Pease River, was represented at every station and comprised 23.8% of the total.
Notropis lutrensis: redhorse shiner. This is also one of the more numerous
and widely distributed species in the Pease River. It was taken from every station
and comprised 17.06% of the total.
Notropis buchanani: ghost shiner. Occurred only at two stations, near the
river mouth. It was taken at West Vernon station in August and September 1956, and
at Vernon Station in August 1956.
Hybognathus placita: plains minnow. Comprising 25.28% of the total, this
widely distributed species was the most abundant of all fishes in the Pease River.
It was not taken at East Vernon Station, but was found at all the other stations.
Pimephales vigilax: parrot minnow. Eleven specimens were taken during
the study, at Vernon and West Vernon Station.
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Pimephales promelas: fathead minnow. Although not numerous, this species
is widely distributed in the Pease, from the headwaters to its mouth.
Family Ameiuridae
Freshwater catfishes
Ictalurus punctatus: channel catfish. A total of ten specimens was taken,
all at West Vernon Station.
Ictalurus melas: black bullhead. This species is not numerous, but well
distributed in the Pease - especially in isolated holes.
Family Cyprinodontidae
Killifishes and topminnows
Fundulus kansae;: plains killifish. The killifish is abundant in the Pease
River and widely distributed.
Cyprinodon rubrofluviatilis; Red River pupfish. Comprising 14.27% of the
total, this salt tolerant species was taken at every sampling station. It was most
abundant at Lazare Station, where the salinity was consistently high.
Family Poeciliidae
Mosquitofishes
Gembusia. affinis: common mosquitofish. <A total of 59 specimens was taken
from three stations. Noteworthy is the collection of one Gambusia at Lazare Station in
March 1957 when the chloride measurement was next-to-the highest recorded during the
entire segment period (13,764 p.p.m.). All of the other specimens of Gambusia were
obtained at Vernon and West Vernon Stations.
Family Centrarchidae
Black basses and sunfishes
Micropterus salmoides; largemouth bass. Only 7 specimens were taken - one
at Quanah Station and 6 at West Vernon Station.
Lepomis cyanellus; green sunfish. Although not abundant, this salt tolerant
sunfish was taken at all but one station. It was absent from only the polluted waters
of East Vernon Station.
Lepomis macrochirus;: bluegill. Not numerous, but widely distributed.
Lepomis humilis: orangespotted sunfish. A total of 99 specimens was taken
at 3 stations.
Lepomis megalotis:; longear sunfish. Fleven specimens were taken at Vernon
and West Vernon Stations.
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Pomoxis annularis;: white crappie. Nine specimens taken, one from Quanah
Station and 8 at West Vernon.
,
Prepared by: Leo D. Lewis Approved by WW pea a
Project Leader Chief Aquatic Biologist
Date; August 7, 1957
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8.
Table 1. Monthly and Annual Mean Discharge at Quanah Station.
(Drainage area, 3,037 square miles, of which 559 square miles is probably noncontributing) .
Year Oct. Nov. Dec. Jan. Feb. March April May June July Aug, Sept. Annual
1924 - - - 10.9 4.97 46.8 99.2 11.4 330 1182 =—-435 579 “
1925 19.4- 0.35 1.63 19.4 4.99 .62 389 1127 51.4 85.3 41160 1063 329
1926 167 ho.4 =. 23 -TL 1.19 35.8 615 105 95.4 266 24.8 451 150
1927 - - - 60.7 18.7 6.25 H7«S «LET 161 18.9 7-16 74.2 -
1928 34.4 0.5 LO 1.0 5.0 ) 2.2 77. 160 197 164 5.6 62.4
1929 - - ~ ~ - - - - - ~ - - 152
1930 94.6 28.9 3.10 11.3 18.3 47.3 120 69.4 .58 3.19 .88 39.7 33.5
1931 1172 20.6 271 16.1 90.3 32.9 81.5 55.0 377 12.8 64.3 Oo 184
1932 182 93.0 63.6 7TH.3 «12.1 53 220 155 2367 = B45 331 184 372
1933 3.86 0 331 11.8 8.19 13.1 202 288 5.10 588 Sah 379 182
1934 81 13.6 9.07 5.87 1.36 20.9 12.3 76.5 128 17-3 311 375 81.0
1935 209 29.5 .81 Ah 1.22 4.95 911 4116 634 90.2 481 173 58h
1936 159 26.8 20.3 11.5 9.51 7:79 9.17 195 86.2 60.9 .99 3563 341
1937 42.5 17-3 16.3 14.0 3.01 3.43 35.4 4.38 640 85.0 1081 281 223
1938 317 14.1 867.39 3.51 23.8 64.7 31.9 563 1616 112 128 6.09 2ho
1939 40.8 33.3 1.64 211 3.14 88.6 295 185 1530 296 273 .02 222
1940 65.3 .03 2.56 2.54 11.2 -16 136° 213 28.1 13.0 830 108 119
1941 39.1 115 1.25 5.33 (19.4 31.8 TAS hook =65531 0137 867 572 1013
1942 2018 111 84.2 38.2 20.0 19.5 1150 60.0 15.5 21.2 36.6 556 346
1943 324 26.2 28.8 23.4 9.38 8.55 69.4 359 46k 12.0 0 6.20 111
1944 8.77 4.37 0 ©6.18.2 16.7 14.9 11.1 6.33 91.3 564 43.4 55.7 68.4 Th .7
1945 33.9 10.1 27.9 19.4% 13.5 16.4 26.8 3.61 76.4% 1030 258 52.9 133
1946 34.0 6.52 5.08 12.9 7.15 1.68 0.63 58.4 331 Wk.O = 332.3 BTL 116
1947 867 34.4 28.5 15.1 4.38 8.18 69.1 2430 57.9 - - - -
Note: All discharge is measured in cubic feet per second.
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9.
Table 2.
Monthly and Annual Run-off at Quanah Station.
(Drainage area, 3037 square miles of which 559 square miles
Year Oct. Nov. Feb. March April May June July Aug. Sept. Annual
192h
1925
1926
1927
1928
1929
1930
1931
1932
1933
1934
1935
1936
1937
1938
1939
1940
1941
19he
1943
1944
1945
1946
1947
1,190
10, 300
2,120
5, 820
72,070
11,180
237
50
5.4
9,790
2,610
19,510
2,510
4,020
2,410
124,100
19,920
539
2,090
2,090
53 330
20.8
2,410
29.8
1,720
1,230
D930
2.4
806
1,750
1,590
1,030
840
1,980
2.0
6, 820
6,630
1,560
260
603
388
2,050
191
16,640
3,910
20 , 330
558
50
1,250
1,000
455
LOL
157
TT
5,180
1,770
1,120
1,710
313
1,750
133
928
286
277
66
1,040
288
1,020
5,020
696
455
76
68
547
167
1, 320
LTD
6h
1,080
1,110
521
858
‘(52
397
243
1,290
30, 410
211
3,980
5,450
9.7
1,950
1,200
526
680
1,010
104
503
9,900
23,120
36,600
2, 840
131
7,140
4,850
13,090
1.2
734
54,220
545
2,110
1,900
57
8,090
kh, 310
68,430
4,130
STU
1,600
37
4,110
702
69,270
6,440
7,170
10,520
4,270
3,380
7,070
17,700
4 , 700
253,100
11,970
26, 950
34,600
11,400
13,090
251, 700
3,690
22 ,070
5,610
222
3,590
149,400
19,600
3,060
5,680
9,570
9,520
35
22,430
140, 800
303
7,590
375 750
35130
58,090
96,150
91,040
1,670
329,100
920
27,640
33,560
4,550
19,670
3,440
72,650
39250
16, 380
1,160
12,140
196
787
51,970
36,130
1,060
5,540
3, THO
5,220
6, 860
18,170
800
8,40
1,300
735
2,670
63, 320
2,710
26, 700
TL, 340
1,520
4LO
10,100
5h
3,950
20 , 370
32,240
19,130
29,590
61
66,480
7,880
16,810
51,010
535320
2,250
)
3,420
15,860
1,980
345
63,270
26, 860
4420
333
236
@)
10,900
22,570
22,290
10, 320
212,000
16, 730
362
1.0
6,400
34,010
33 ,080
369
4,070
3,150
51,850
238,100
108, 500
45,300
110,000
2h, 300
133,400
270,100
131,500
58,640
422 , 800
24-7, 800
161,500
174,100
160, 700
86,050
733,500
250,200
80, 680
54.190
96,060
83,920
a meena mreraeeeaeeeeeeniremnareemaceeneareerreeeereeeenenmnenmememmemmmenemmetmmemnemamenmnnenemenmmnnrmenmmmnnmennnen se rnreeeee RR NNTTEE ECT TOE Ee Te
Note:
All run-off is measured in acre feet,
eee
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10.
Table 3. Chemical Nature of the Water at the Sample Station.
Total
Date Calcium Sodium Chloride Sulfate Carbonates Bicarbonates Salts pH
NORTH FORK STATION
6/19/57 216 300 505 382 0 102 1505;
7/11/56 732 1050 1597 LTLT 6) 61 5187 -
8/22/56 878 1173 1864 1939 fe) 124 5978 —s«7.4
9/15/56 90h, 1683 3461 874 @) 162 7084 7.15
11/27/56 156 2423 3852 1548 6) 157 8736 7.8
12/27/56 864 1709 3160 1228 fe) 180 T1412 88.3
1/9/57 1120 1919 = 2973 2539 18 134 8703 8h
2/7/57 1020 1664 2734 2093 12 14h 7667 8.0
3/26/57 784 1617 2521 1743 9 108 6782 7.78
4/12/57 828 1632 2570 1824 6 108 6968 7.75
5/2h/57 704 2457 3873 1459 12 132 8637 7.80
MATADOR STATION
6/19/56 300 140 200 538 fe) 5h 1232 -
7/11/56 624 498 809 1320 0) 158 3409 -
8/22/56 dry
9/15/56 ary
11/27/56 = ary
SOUTH FORK STATION
12/27/56 = ary
1/9/57 dry
2/7/57 dry
3/26/57 dry
4/12/57 dry
5/24/57 292 121 195 590 6 116 1320 7-97
LAZARE STATION
6/19/56 300 560 950 516 @) 108 23h -
7/11/56 992 3250 5059 2328 ) 122 11751_—sé-
8/22/56 2195 9246 14697 4531 6) 216 30884 7.25
9/15/56 1318 5829 10895 471 ) 162 18675 7.65
11/27/56 1536 6565 10206 3446 0) 183 21936 «77.7
12/27/56 1672 7515 11804 3600 ) 168 23759 «8.4
1/9/57 2048 8150 12780 522 18 122 27640 8.5
2/7/57 2082 8333 12958 4738 18 126 28255 8.1
3/26/57 1634 8232 =. 13 764 2367 12 132 26141 7.70
4/12/57 1592 8190 12567 3811 6 126 26292 = 7.55
5/2/57 426 891 1530 730 0) 110 3687 ~=—s-: 7.87
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Table 3. (Continued).
“SO ae
ute Calcium Sodium Chloride Sulfate Carbonates Bicarbonates Salts pH
$e
QUANAH STATION
6/19/56 928 1600 2911 1h64 @) 230 7133 7
7/11/56 640 1500 2547 1160 0 92 5939 “
8/22/56 278 150 195 634 ) 104. 1361 7.3
9/15/56 3hh 220 343 662 6) 204 1773 7.80
11/27/56 756 1887 2787 1709 6) 344 74.83 7-6
12/27/56 1204 2887 5015 2035 6) 126 11267 8.3
1/9/57 1428 2814 4h38 3173 18 124 11995 8.2
2/7/57 1508 3341 5503 3015 12 150 13529 8.1
3/26/57 1128 3213 52ho 2199 9 134 12923 7.60
4/12/57 936 1581 = 2734 1764 6 96 7117 ~—s«7..81
5/24/57 22h 182 327 384 6 102 1225 8.03
WEST VERNON STATION
——————
6/19/56 816 1250 2157 1497 fe) 198 5918 ie
7/11/56 308 345 639 509 fe) 110 19lli-
8/22/56 248 180 231 590 ) 90 1339 =: 77.8
9/15/56 302 162 238 624 0) LA5 L471 7.65
11/27/56 588 936 1456 1205 ) ahh 4hueag 8.0
12/27/56 332 h52 682 720 6) 126 2312 8.3
‘9/57 696 896 1430 1373 30 ohh 4669 = 8.1
457 796 1089 1669 1714 18 2ho 5526 7.8
3/26/57 1046 3654 5630 2400 12 1he 12884 7.80
4/12/57 500 603 1044 Qh 6 126 3220 7.92
5/24/57 230 143 277 413 6 72 1141 8.00
VERNON STATION
6/19/56 952 1500 = 2574 1834 0 128 6988 -
7/11/56 192 156 355 2ho 6) 85 1028 i=
8/22/56 22h 126 160 518 fe) 8h 1112 7.5
9/15/56 456 816 1598 643 ) 186 3699 =—s-'7.75
11/27/56 620 975 1527 1344 9) 157 4623 7.9
EAST VERNON STATION
1/7/57 32h 368 632 585 fe) 132 2041 88..3
1/23/57 180 180 204 96 30 kok 1184 7.4
2/7/57 134 180 160 6h 0 522 1060s 7.4
3/26/57 930 2205 3841 1512 18 126 8632 8.0
4/12/57 298 309 487 1834 12 183 3123 += 8.0
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Table 4.
Date
6/19/56
7/11/56
8/22/56
9/15/56
11/27/56
12/27/56
1/9/57
2/7/57
3/26/57
4/12/57
5/24/57
6/19/56
7/11/56
8/22/56
9/15/56
11/27/56
12/27/56
1/9/57
2/7/57
3/26/57
4/12/57
5/24/57
6/19/56
7/11/56
8/22/56
9/15/56
11/27/56
12/27/56
1/9/57
2/7/57
3/26/57
4/12/57
5/2h/57
12.
Physical Conditions at the Sample Stations.
Air Temp.
99
99
dry
dry
dry
ary
ary
ary
dry
76
99
oT
1oh
68
64
5L
ko
33
19
Water Temp.
NORTH FORK STATION
86
82
72
81
52
48
5h
50
52
47
69
MATADOR STATION
88
91
SOUTH FORK STATION
70
LAZARE STATION
86
TT
a
86
46
46
29
52
22
dh
67
Turbidity (mm.)
15
100
100 - very low - not running
210 - much reduced
600
622 - not running, holes
only
666
808
1000 plus
755
160
oo)
35
ho
35
120
185
500 - running, but very
shallow
1000 plus
1000 plus
1000 plus
1000 plus
1000 plus
1000 plus
4O - (Water too high and
swift to seine
efficiently).
--- Page 13 ---
Table 4.
13.
Physical Conditions at the Sample Stations (Continued).
teen
Date
Air Temp.
Water Temp.
Turbidity (mm.)
net niente
6/19/56
7/11/56
8/22/56
9/15/56
11/27/56
12/27/56
1/9/57
2/7/57
3/26/57
4/12/57
5/24/57
6/19/56
7/11/56
8/22/56
9/15/56
11/27/56
_ 27/56
1/9/57
2/7/57
3/26/57
4/12/57
5/24/57
6/19/56
7/11/56
8/22/56
9/15/56
11/27/56
12/27/56
1/9/57
2/7/57
3/26/57
4/12/57
5/24/57
95 81
81 73
97 19
104 77
59 43
te) 38
65 5h.
53 48
55 43
y)
Water to high to seine.
QUANAH STATION
135
20 - raining heavily
60 - muddy from recent rain
170 - much reduced in area
360
360
260
1000 plus
765
290
WEST VERNON STATION
93 81
72 73
90 75
90 TT
4S 39
ho 37
64. 5h
ie) A7
5h 39
34 dh
‘Yd: 7
88 81
19 73
90 72
90 77
50 he
he 37
VERNON STATION
520
60 - raining heavily
120 - recently rained
95 - much reduced in area
3
665
2h0
320
330
2h0
60 - High water prevented seining.
Still rising.
390
hO - recently rained
75 - recently rained
210 - much reduced
370
455
EAST VERNON STATION
56 53
dry
51 39
dry
380
310
Station inaccessible - roads washed out
--- Page 14 ---
14.
Table 5. Monthly Variation in Species and Numbers of Fishes at North Fork Station, Pease
River.
of
Species 6/19 7/11 8/22 9/15 11/27 12/27 1/9 2/7 3/26 4/12 5/24 Total Total
N. potteri 1 i OF
N. bairdi 20 4 179 60 61 22 he 388 = 25.33
N. lutrensis 2 7 7 34 79 Ye a7 ll 23 21 205: 13.38
Hybognathus 7. 209 224 2h 10 12 16 7 8 581 37.92
P. promelas 9 3 #& 16 1.04
F. kansae lL 2 12 21 33 8 10 4H 7 98 6.40
Cyprinodon 46 17 61 9 ak 3 63 223 14.56
L. cyanellus Lo 1 2 13 7 2 18 1.17
L. macrochirus 2 2 0.13
Total 4 148 220 267 295 12h 198 75 113 10 78 1532 100.00
% of Total 0.3 9.7 14.4.17.3 19.3 8.1 12.94.9 7.4 .6 5.1 100.00
--- Page 15 ---
15.
Table 6. Monthly Variation in Species and Numbers of Fishes at Matador Station and
South Fork Station, Pease River.
* % ** Ke HH OHH HE KK
? of
Species 6/19 7/11 8/22 9/15 11/27 12/27 1/9 2/7 3/26 4/12 5/2h Total ‘Total
N. bairdi 1 4 5 1.45
N. lutrensis 62 21 83 2h .06
Hybognathus 30 9 kg 88 25.51
P. promelas 9 16 25 7-25
I. melas 21 ho 1 62 17.97
F. kansae 33 33 9.56
L. cyanellus 14 21 ; 35 10.14
Total 169 108 68 345 100.00
% of Total 49.0 31.3 19.7 100.00
rn
* Matador station dry.
** South Fork Station dry.
Note: Matador station discontinued in November - replaced by South Fork Station.
_
--- Page 16 ---
16.
Table 7. Monthly Variation in Species and Numbers of Fishes at Lazare Station, Pease Rive
Species
Dorosoma
Hybopsis
N. potteri
bairdi
lutrensis
Hybognathus
F. kansae
Cyprinodon
Gambusia
_pareonowaaer TaN NETS
L. cyanellus
Tr.
N.
Total
% of Total
of
6/19 7/11. 8/22 9/15 11/27 12/27 1/9 2/7 3/26 4/12 5/2k Total Total
36
108
182
34h
1
>
el 1 15
1
16 82 206
TX) 26 «031
37 105 55
1
121 215 307
1.5 2.6 3.8
673
50
265
1013
12.4
1066
k
492
370
1932
23.6
121
166
45k
743
9.1
al
865
135
L021
12.5
193
D902
481
1227
15.0
350
363
499
1212
14.8
45
1
2
10
2505
3
393
2669
2591
i
2
8180
-O1
-06
.12
30.62
-O4
4.80
32.63
31.67
-O1
.02
99.98
100.00
--- Page 17 ---
17.
ble 8. Monthly Variation in Species and Numbers of Fishes at Quanah Station, Pease River.
* of
Species 6/19 7/11 8/22 9/15 11/27 12/27 1/9 2/7 3/26 4/12 5/2h Total Total
Dorosoma 1 25 1 27 -69
Carpiodes 1 1 -03
Hybopsis 2 13 5 2 23 59
N. percobromus 3 2 5 213
N. potteri 1 15 1 17 43
N. bairdi 11 4 23 46k 861700 53 257 908 23.20
N. lutrensis 27 16 18 8 9 jl 102 62 7 320 «8.18
Hybognathus 111 38 276 301 374 542-352 66 192 251 2503 63.91
P. promelas 2 1 3 08
T. melas 5 1 6 215
F. kansae 22 20. «7 2 dl a 55 1 AL
Cyprinodon 1 2 1 4 10
Micropterus 1 1 03
L. cyanellus 11 8 6 1 26 °~=>—- 66
L. macrochirus 2 2 605
L. humilis 3 9 12 231
Pomoxis 1 1 -03
Total 176 89 317 378 852 568 493 211 312 518 3914 99.98
% of Total L5 2.3 8.1 9.7 21.8 14.512.6 5.4 8.0 12.2 99.9
sar ne nse einreereen vn pues es se
* Seining attempted, but produced nothing. Water too high, swift and muddy.
--- Page 18 ---
18.
Table 9. Monthly Variation in Species and Numbers of Fishes at West Vernon Station,
Pease River.
% % of
Species 6/19 7/11 8/22 9/15 11/27 12/27 1/9 2/7 3/26 4/21 5/24 Total Total
Dorosoma 5 3 20 1 4 33 -68
Carpiodes 1 21 63 9 oh. 1.95
Cyprinus 2 6 4 12 625
Hybopsis. 1 4 2 1 1 9 18
N. percobromus 4 2 1 4 11 23
N. brazosensis h h .08
NV. potteri 1 5 29 3 2 ko 83
WV. bairdi 5 126 8678 87 =323)—C oa 5 635 13.16
WN. lutrensis 38 17 136 201 kL 69 138 1262 188 195 2285 47.36
N. buchanani 80 26 106 2.20
Hybognathus 27 7 11 482 «19 158 26 548 57 1335 27.67
P. vigilax 6 2 8 16
f. promelas 2 9 11 223
TI. punctatus 1 6 3 10 21
I. melas 1 hO 8=—-3 64 1.33
F. kansae 3 1 h -08
Cyprinodon 2 10 2 14 .29
Gambusia 1 11 9 1 22 46
Micropterus 1 2 3 6 ”
L. cyanellus 3 T 2 18 30 ea
LT. macrochirus 6 1 2 2 3 14 .29
LL. humilis 2 6 6 19 ak 2 1 60 1.24
L. megalotis 2 5 1 2 10 -21
Pomoxis 1 1 2 k 8 16
Total 59 85 304 426 665 189 465 1617 751 264 4.825 100.00
% of Total 1.2 1.8 6.3 8.8 13.8 3.9 9.6 33.5 15.6 5.5 100.00
* River at flood stage. Impossible to seine.
--- Page 19 ---
19.
ole 10. Monthly Variation in Species and Numbers of Fishes at Vernon Station, Pease River.
Species 6/19 7/11 8/22 9/15 11/27 12/27 Total 4% of Total
Dorosoma 3 1 1 5 42
Carpiodes 13 8 1 22 1.83
Hybopsis 4 50 3 57 4.75
N. potteri 10 10 .83
N. bairdi 16 8 263-36 323 26.94
N. lutrensis Ta 101 216 68 31 54 511 ho .62
N. buchanani 3 3 25
Hybognathus 11 16 28 9 90 3 157 13.09
P. vigilax 3 3 25
P. promelas 13 13 1.08
I. melas 5 3 8 -67
Cyprinodon 4 4 33
Gambusia 16 11 7 2 36 3.00
L. cyanellus 1 1 3 7 6 18 1.50
ZL. macrochirus a. 1 .08
L. humilis 4 9 5 9 27 2.25
L. megalotis 1 1 .08
tal 89 137 288 122 453 «110 1199 99.8
% of Total 74 11.4 2h.o 10.2 37.8 9.2 100.00
Note: Station discontinued in January - replaced by East Vernon Station.
eee
--- Page 20 ---
20.
Table 11. Monthly Variation in Species and Number of Fishes at East Vernon Station, Pease
River.
¥* HE HH Ke
Species 1/9 2/7 3/26 4/12 5/2h Total % of Total
N. bairdi 3 3 30.00
N. lutrensis 3 3 30.00
Cyprinodon 4 4 40.00
Total 10 10 100.00
* Five drags produced only one live fish (Hybognathus - very sick). Present in the
water and along the bank were dead carp, carpsucker, bullhead catfish and minnows.
The minnows were either too dehydrated or decomposed to identify.
HX Sick carp and carpsucker observed. Water appeared too unsanitary to seine.
Collected chemical and physical data only.
*#** Considerable seining produced nothing.
¥*¥e*% River at flood stage - impossible to seine.
--- Page 21 ---
el.
-able 12. Total Numbers of Fish Taken at the Pease River Stations.
ea Ce eee
Species North Matador and Lazare Quanah West Vernon East Total % of
Fork South Fork Vernon Vernon Total
Dorosoma 33 5 re) 1 27 ) 9) 66 33
Carpiodes oh 22 ©) 0 1 0 ) 117 58
Cyprinus 12 6) 0 0 ) ) ©) 12 06
Hybopsis 9 57 ) 5 23 0 0 oh AT
N. percobromus 11 @) 0 ae) 5 @) ) 16 .08
N. brazosensis 4 @) ) ) @) ) ) 4 .02
N.potteri ho 10 6) 10 17 1 6) 78 239
N. bairdi 635 323 3 2505 908 388 5 4767 23.83
NV. lutrensis 2285 511 3 3 320 205 83 3410 17.06
N. buchanani 106 3 0) ) 0 0 0 109 ok
Hybognathus 1335 157 0) 393 2503 581 88 5057 25.28
P. vigilax 8 3 0 0 0 0 0 11 .05
P. promelas 11 13 ) @) 3 16 25 68 34
T. punctatus 10 0 @) 0 @) ) fe) 10 05
T. melas 64 8 ) 0 6 ) 62 140 70
F. kansae 4 9) 0 2669 55 98 33 2859 14.29
Cyprinodon 1h 4 4 2591 4 223 14 2,854 14.27
Gambusia 22 36 ) 1 0 ) 0 59 .29
‘Leropterus 6 @) ) ) 1 ) @) 7 203
uo. cyanellus 30 18 ) 2 26 18 35 129 64
L. macrochirus 1 1 @) @) 2 2 @) 19 .09
L. humilis 60 aT ) 0 12 0 ) 99 4g
L. megalotis 10 1 fe) 0 0 0 6) 11 .05
Pomoxis 8 0 0) 0 1 ) 0 9 .O4
Total 4.825 1199 10 8180 3914 1532 345 20,005 99.97
% of Total 24.12 6.0 @) (+) 40.9 19.6 7.7 1.7 100.00
--- Page 22 ---
SSeS <= oininiey eee —=_em om a=
eae eemleane ao =o = oo @ Fy
OKLAHOMA
' 4
id t
' 4
BRS ESS | @HiLoRESS 5 NSO
' HALL ! ) RIVE
a t a) 1s
0 ry j -
} Plg' as
es So eben LL ay, a t Le |
: y ‘ EF 0
t v 4 « cf ~ Ga, OYo" =
ef i G@otTree We Pe ;
FlLloybD aor AOS hg ‘ WILBARGER
--- Page 23 ---
Treated sewage effluent from the city of Vernon. This
water is well treated, free of all solids and clear.
Vernon's sewage effluent ditch just before entering
river. Turtles, frogs and algae were observed in the
ditch.
--- Page 24 ---
West Vernon Station under normal conditions.
West Vernon Station during rise.
--- Page 25 ---
sec nm mers ohn
.
North Fork Station. River is usually dry here, and
collections were taken from isolated pools below cliffs
on the left.
South Fork Station following recent rise. This is the
only time during the segment that water was found to be
present. Note tree growing in middle of river bed.