(1956–1957) 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 B
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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 Invento 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 labore-
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 Mctley 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 northern
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 Quansh 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
inte 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-
erilal 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. ‘It
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 Hybognethus 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 6 149 110 8.4
CHEMICAL CHARACTERISTICS OF WATER
The chemical nature of water at the samplé 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 dity 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 direct-
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 (0.3% 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 23.84 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.
Notreopis 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 Fast Vernon Station, but was found at all the other stations.
Pimephales vigilax: rrot 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.
rinodon 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 Gembusia 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 Quaneh 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 § at West Vernon.
/ ¢ o—
Prepared by: ’ Leo D. Lewis Approved by VZAl AtiAwW —
Project Leader ' Chief Aquatic Biologist
Date: August 7, 1957 a
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8.
Table 1. Monthly and Annual Mean Discharge at Quansh Station.
Drainage area, 3,037 square miles robably noncontributing).
Year Oct. Nov. Dec. Jan. Feb. March April May June July Aug. Sept. Annual
1924. - - - 10.9 k.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) «4551.4 = 85.3 = 1160S: 1063 329
1926 167 hook = 23 neck 1.19 35.8 615 105 95.4 266 24.8 451 150
1927 - - - 60.7 18.7 6.2 47.8 .117 161 18.9 7.16 74.2 -
1928 34.4 0.5 1.0 1.0 5.0 ) 2.2 171 160 197 164 5.6 62.4
1929 ~ - - . . ~ - ~ - - - - 152
1930 94.6 28.9 3.10 tis3, 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 12.86 64.3 Oo 184
1932 182 93.0 63.6 74.300 «12.1 53 220 155 2367 8h5 331 184 372
1933 3.86 .O 331 11.8 8.19 13.1 .02 288 5.10 588 52h 379 182
1934 81 13.6 9.07 5.87 1.36 20.9 12.3 76.5 128 7.3 «=F 375 81.0
1935 .09 29.5 .81 yy 1.22 495 911 411 634 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 35.4 438 640 85.0 1081 281 223
1938 317 VWA.1. = -7.39 3.51 23.8 64.7 31.9 563 1616 112 128 6.09 ako
1939 4o.8 ~ 33.3 1.64 211 3.14 88.6 -95 185 1530 296 273 .02 222
19h0 65.3 .03 2.56 2.54 11.2 116 136° 213 28.1 13.0 830 108 119
1941 39.1 115 1.25 5.33 19.4 31.8 745 hook §=655531 137 867 572 1013
1942 2018 = i 84.2 38.2 20.0 19.5 1150 60.0 15.5 21.2 36.6 556 346
1943 32h 26.2 28.8 23.4 9.38 8.55 69.4 359 464 12.0 0O 6.20 111
1944 So: 77 4.37 18.2 16.7 14.9 1.1 6.33 91.3 564 43.4 55.7 68.4 74.7
1945 33.9 10.1 #7.9 19.4 13.5 16.4 26.8 3.6 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 4.0) ©=— 32.32 87 116
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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Table 2. Monthly and Annual Run-off at Quanah Station.
Drainage area, 3037 square miles of which 559 s miles is probably noncontributing).
fear Oct. Nov. Dec. Jan. Feb. March April May June July Aug. Sept. Annual.
geh.- - - 668 286 2,880 5,900 702 19,600 72,650 26,700 Bu50C~C‘iYS
925 1,190 20.8 100 ~=1,190 277 38.1 23,120 69,270 3,060 5,250 71,340 63,270 238,100
926 10,300 2,410 14.1 43.6 66 2,200 36,600 6,440 5,680 16,380 1,520 26,860 108,500
97 - - - 3,730 1,040 30h 2,80 7,170 9,570 1,160 Kho 420 -
928 2,120 29.8 61.5 61.5 288 ) 131 10,520 9,520 12,140 10,100 333 45, 300
g29 - - - - - - - - - - - ~ 110,000
930 5,820 1,720 191 695 1,020 2,910 7,140 4,270 35 196 5h 236 aly, 300
931 72,070 1,230 16,6ho0 990 5,020 2,020 4,850 3,380 22,430 787 3,950 Oo 133, ’ i100
.932 11,180 5,530 3,910 4,570 696 33 13,090 7,070 140,800 51,970 20,370 10,900 270,100
933 237 2.4 20 , 330 726 455 806 1.2 17,700 303 36,130 32,240 22,570 131,500
934 50 806 558 361 76 1,290 734 4,700 7,590 1,060 19,130 22,290 58,640
935 5.4 1,750 50 27 68 30,410 54,220 253,100 37,750 5,540 29,590 10,320 422,800
.936 9,790 1,590 1,250 705 S47 479 545 11,970 5,130 3,740 61 212,000 27,800
937 2,610 1,030 1,000 860 167 211 2,110 26,950 58,090 5,220 66,480 16,730 161,500
938 19,510 840 455 216 1,320 3,980 1,900 34,600 96,150 6,860 7,880 362 174,100
939 2,510 1,980 101 13,000 175 5,450 57 11,400 91,040 18, 170 16,810 1.0 160, 700
940 4,020 2.0 157 156 644. 9.7 8,090 13,090 1,670 800 51,010 6,400 86,050
QL 2,410 6,820 77 328 1,080 1,950 44,310 251,700 329,100 8,440 53,320 3.010 733, 500
gue 124,100 6,630 5,180 2,350 1,110 1,200 68,430 3,690 920 1,300 2,250 33,080 250,200
9h3 19,920 1,560 1,770 1,440 521 526 4,130 22,070 27,640 735 fe) 369 80, 680
hy. 539 260 1,120 1,030 858 680 377 5,610 33,560 2,670 3,420 .,O70 54,190
O45 2,090 603 1,710 1,190 752 1,010 1,600 222 4,550 63,320 15,860 3,150 96 ,O60
G46 2,090 388 313 793 397 10h 37 3,590 19,670 2,710 1,980 51,850 83,920
7 53,330 2,050 1,750 928 243 503 4,110 149,400 3,440
Tote; All run-off is measured in acre feet.
— Eee
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LU.
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 1747 0 61 5187 -
8/22/56 878 1173: 1864 1939 fe) 124 5978 TA
9/15/56 904 1683 3461 874. ) 162 7084 1°15
11/27/56 756 2423 3852 1548 0) 157 8736 7.8
12/27/56 864 1709 3160 1228 fe) 180 TLbL 8.3
1/9/57 1120 1919 2973 2539 18 134 8703 8.4
2/7/57 1020 1664 2734 2093 12 uhh 7667 8.0
3/26/57 78h 1617 2521 1743 9 108 6782 =: 7.78
4/12/57 828 1632 2570 1824 6 108 6968 ~—s«- 7.75
5/2h/57 70} 2457 3873 1459 12 132 8637 7.80
MATADOR STATION
6/19/56 300 140 200 538 ) 5k 1232 -
7/11/56 624. 498 809 1320 f°) 158 3409 -
8/22/56 dry
9/15/56 dry
11/27/56 = ary
SOUTH FORK STATION
12/27/56 ary
1/9/57 ary
2/7/57 dry
3/26/57 ary
4/12/57 dry
5/2k/57 292 121 «195 590 6 116 1320 7.97
LAZARE STATION
6/19/56 300 560 950 516 re) 108 2h 3h -
7/11/56 992 3250 5059 2328 0 122 11751;
8/22/56 2195 92h6 14697 4531 ) 216 30884 7.25
9/15/56 1318 5829 10895 wal fe) 162 18675 7-65
11/27/56 1536 6565 10206 3446 fe) 183 21936 =—«7..7
12/27/56 1672 7515 11804 3600 ) 168 23759 «8h
1/9/57 2048 8150 12780 450 18 122 27640 8.5
2/7/57 2082 8333 12958 4.738 18 126 28255 8.1
3/26/57 1634 8232 13764 2367 12 132 26141 7.70
4/12/57 1592 8190 12567 3811 6 126 26292 = 7.55
5/24/57 426 891 1530 730 fe) 110 3687 7.87
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Table 3. (Continued).
Total
Date Calcium Sodium Chloride Sulfate Carbonates Bicarbonates Salts pH
QUANAH STATION
6/19/56 928 1600 2911 1464 fe) 230 7133 -
7/11/56 640 1500 = 2547 1160 0 92 5939—éi«
8/22/56 278 150 195 634 fo) 104 1361 73
9/15/56 344 220 343 662 0 20k L773 7.80
11/27/56 756 1887 2787 1709 ©) 34h 7483 7.6
12/27/56 1204 2887 5015 2035 9) 126 11267 8.3
1/9/57 1428 281h 4438 3173 18 12 11995 8.2
2/7/57 1508 3341 5503 3015 12 150 13529 8.1
3/26/57 1128 3213 452ko 2199 9 134 12923 7.60
4/12/57 936 158. 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 ) 198 5918 -
7/11/56 308 345 639 509 fe) 110 1911 -
8/22/56 2h8 180 231 590 ) 1339 7.8
9/15/56 302 162 238 62h 0 145 1471 7.65
11/27/56 588 p38 1456 1205 0 ahh 42g = 8.0
12/27/56 332 52 682 ) 126 2312 8.3
1/9/57 696 896 1430 1373 30 ahh 4669 = 8.1
2/7/57 796 1089 1669 171k 18 2ho 5526 «7.8
3/26/57 1046 3654 5630 2h00 12 lhe 12884 7.80
4/12/57 500 603 1044 41 6 126 3220 7-92
5/24/57 230 143 277 413 6 T2 111 8.00
VERNON STATION
6/19/56 952 1500 257k 1834 0 128 6988 -
7/11/56 192 156 355 2ko ) 85 1028 -
8/22/56 22h 126 160 518 9) 8h 1112 7-5
9/15/56 456 816 1598 643 0 186 3699-775
11/27/56 620 975 1527 134y 0 157 4623 7.9
BAST VERNON STATION
1/7/57 32h 368 632 585 0 132 2041 8.3
1/23/57 180 180 204 96 30 kok 1184 7-4
2/7/57 134 180 160 64 ) 522 1060 TA
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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12.
Table 4. Physical Conditions at the Sample Stations.
Date Air Temp. Water Temp. Turbidity (m.)
NORTH FORK STATION
6/19/56 95 86 15
7/11/56 95 82 100
8/22/56 95 72 100 - very low - not running
9/15/56 102 81 210 - much reduced
11/27/56 val 52 600
12/27/56 64. 48 622 - not running, holes
only
1/9/57 76 5h 666
2/7/57 61 50 808
3/26/57 60 52 1000 plus
4/12/57 37 \7 755
5/24/57 73 69 160
MATADOR STATION
6/19/56 99 88 ks
7/11/56 99 gl 35
8/22/56 dry
9/15/56 dry
11/27/56 ary
SOUTH FORK STATION
12/27/56 ary
1/9/57 dry
2/7/57 dry
3/26/57 ary
4/12/57 ary
5/24/57 76 70 ho
LAZARE STATION
6/19/56 95 86 35
7/11/56 90 TT 120
8/22/56 97 79 185
9/15/56 104 86 500 - running, but very
shallow
11/27/56 68 h6 1000 plus
12/27/56 51 46 1000 plus
1/9/57 6h 59 1000 plus
2/T/5T 51 52 1000 plus
3/26/57 kg 55 1000 plus
4/12/57 33 a 1000 plus
5/24/57 79 67 ho - (Water too high and
swift to seine
efficiently).
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13.
Table 4. Physical Conditions at the Sample Stations (Continued).
Date Air Temp. Water Temp. Turbidity (m.)
QUANAH STATION
6/19/56 95 61 135
7/11/56 81 73 20 - raining heavily
8/22/56 97 79 60 - muddy from recent rain
9/15/56 104 TT 170 - much reduced in area
11/27/56 59 43 360
12/27/56 kg 38 360
1/9/57 65 54 260
2/T/5T 53 48 1000 plus
3/26/57 55 43 765
4/12/57 35 38 290
5/24/57 Water to high to seine.
WEST VERNON STATION
6/19/56 93 81 520
7/11/56 Te 73 60 - raining heavily
8/22/56 90 75 120 - recently rained
9/15/56 90 qT 95 - much reduced in area
11/27/56 45 39 380
12/27/56 ke 37 665
1/9/57 6h, 5h 2hO
2/7/57 kg kT 320
3/26/57 5h 39 330
4/12/57 34 hh 2ho
5/24/57 7 71 60 - High water prevented seining.
Still rising.
VERNON STATION
6/19/56 88 81 390
7/11/56 79 73 ho - recently rained
8/22/56 90 72 75 - recently rained
9/15/56 90 TT 210 - much reduced
11/27/56 50 he 370
12/27/56 ke 37 k55
EAST VERNON STATION
1/9/57 56 53 360
2/7/57 dry
3/26/57 51 39 310
dry
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
ee
N. potteri ~ | 1 07
N. bairdi 20 & 179 60 61 22 he 388 = - 5.33
N. lutrensis 2 7 7 34 7729 Ye 27 1 23 ~#21 205 13.38
Hybognathus 7l 209 22k ak 10 12 16 7 8 581 37.92
P. promelas 9 3 4 16 1.04
F. kansae 1 2 12 2 33 8 lo hk 7 98 6.40
Cyprinodon L6 17 61 9 ak 3 63 223 14.56
L. cyanellus 1 1 a 2 1 3 T 2 18 117
L. macrochirus 2 2 0.13
Total 4 148 220 267 295 12h 198 75 113 10 78 1532 100.00
eee
% of Total 0.3 9-7 14.4.17.3 19.3 8.1 12.94.9 7.4 .6 5.1 100.00
rrr cee sn seen nenneerenenrerencnnneneenen
--- Page 15 ---
15.
Table 6. Monthly Variation in Species and Numbers of Fishes at Matador Station and
South Fork Station, Pease River.
Ke ee #* KX HH XE of
Species 6/19 7/11 3/22 ofS 11/27 12/27 1/9 2/7 3/26 k/12 5/2k Total ‘Total
N. bairdi 1. L 5 (1.45
N. lutrensis 62 a1 83 2k .06
Hybognathus 30 9 4g 88 25.51
P. promelas 9 16 25 7.25
I. melas 21 Lo 1 62 17.97
F. kansae 33 33 9.56
L. cyanellus 14 21 35 10.14
Total 169 108 68 345 100.00
%4 of Total kg.0 31.3 | 19.7 100.00
* 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 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 i OL
Hybopsis 5 5 .06
N. potteri - 10 10 12
N. bairdi 36—=C i iL 15 673 1066 121 21 193 350 8 2505 30.62
N. lutrensis 2 1 3 -O4
Hybognathus 16 16 82 206 50 4 2 i? 393 4.80
F. kansae 108 40 26 31 ah 492 166 865 552 363 2 2669 32.63
Cyprinodon 182 37 105 55 265 370 454 135 481 gq 8 2591 31.67
Gambusia i uh OL
L-c ellus 1 1 2 -02
Total 344 121 215 307 1013 1932 743 1021 1227 1212 45 8180 99.98
% of Total 4.2 1.5 2.6 3.8 12.4 23.6 9.1 12.5 15.0 14.8 .5 100.00
— i teense
--- Page 17 ---
Table 8. Monthly Variation in Species and Numbers of Fishes at Quamah Station, Pease River.
of
Species 6/19 7/11 8/22 9/15 11/27 12/27 1/9 2/7 3/26 4/re sak Total Total
Dorosoma 1 25 I. 27 -69
Carpiodes ne 1 .03
Hybopsis 2 13 5 2 23 -59
N. percobromus 3 2 5 +13
N. potteri 1 15 1 17 43
N. bairdi 11 4 23 461 17 hi. Aa 53 257 908 23.20
N. lutrensis 27 16 18 8 9 TL 102 62 7 320 «=—(:88..18
bognathus pls Be 3 38 276 301 374 5u2. 352 66 192 251 2503 63.91
P. promelas 2 1 3 -08
I. melas & 2 6 15
F. kansae 22 20 7 2 1 3 55 1.41
Cyprinodon 1 2 1 4 -10
a 1 ZL .03
cyanellus 11 8 6 1 26 -66
r. macrochirus 2 2 205
L. humilis 3 9 12 -31
Pomoxis q. 1 -03
Total 176 89 317 378 852 568 493 211 312 518 3914 99.98
% of Total 45 2.3 8.1 9.7 21.8 14.512.6 5.4 8.0 12.2 99.9
* Seining attempted, but produced nothing. Water too high, swift and muddy.
17.
--- 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 11/2712/27 1/9 2/7 3/26 4/21 5/2k Total Total
Dorosoma 5 3 20 2 k 33 -68
Carpiodes al 2. 63 9 oh 1.95
Cyprinus 2 6 12 225
Hybopsis 2 k 2 1 1 9 .18
N. percobromus h 2 1 k 11 .23
N. brazosensis h h .08
N. potteri 1 5 29 3 2 ko 83
N. bairdi 5 126 «678 87 323 l 5 635 13.16
NV. Lutrensis 38 17 136 201 41 69 138 1262 188 195 2285 47.36
W. buchanani 80 26 106 2.20
Hybognathus 27 7 11 482 «619 158 26 548 57 1335 27.67
P. vigilax 2 8 .16
P. promelas 2 9 11 23
I. punctatus 1 6 3 10 21
I. melas 1 4O 8-83 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 12
L. cyanellus 3 7 2 18 30 .62
E. macrochirus 6 1 2 2 3 14 .29
L. humilis 2 6 6 19 a 2 1 60 1.24
L. megalotis 2 5 1 2 10 ‘2.
Pomoxis 1 1 2 h 8 16
Total 59 85 304 26 665 189 465 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.
Table 10. Monthly Variation in Species and Numbers of Fishes at Vernon Station, Pease River.
Species 6/19 7/11 8/ee 9/15 11/27 12/27 Totel 4% of Total
Dorosoma 3 1 1 5 .4o
Carpiodes 13 8 1 22 1.83
Hybopsis 4 50 3 57 “D
N. potteri 10 10 .83
N. bairdi 16 8 263 «36 323 26 .9h
WN. lutrensis hy 101 216 68 31 54 511 he .62
N. buchanani 3 3 +25
Hybognathus 11 16 28 ) 90 3 157 13.09
P. vigilax 3 3 25
P. promelas 13 13 1.08
I. melas 5 3 8 .67
Cyprinodon 4 h 33
Gambusia 16 11 T 2 36 3.00
L. cyanellus 1 1 3 7 6 18 1.50
L. macrochirus 1 1 -08
L. humilis 4 9 5 9 27 2.25
L. megalotis 1 3. -08
Total 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.
* ee Se XE
Species 1/9 2/7 3/26 4&/le 5/2h Total 4% of Total
N. bairdi 3 3 30.00
N. lutrensis 3 3 30.00
Cyprinodon y 4 kO.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.
HE Sick carp and carpsucker observed. Water appeared too unsanitary to seine.
Collected chemical and physical data only.
*e* = =©6 Considerable seining produced nothing.
eee River at flood stage - impossible to seine.
--- Page 21 ---
el.
Table 12. Total Numbers of Fish Taken at the Pease River Stations.
Species North Matador and Lazare Quanah West Vernon East Total % of
Fork South Fork Vernon Vernon Total
Dorosoma 33 5 0 z 27 0 0 66 33
Carpiodes ok 22 0 @) 1 @) ¢) Ly 58
Cyprinus 12 fe) ) fe) fe) 0 0 12 06
Hybopsis 9 57 ) 5 23 @) @) ok 47
N. percobromus 11 @) fo) ) 5 fe) 0 16 .08
N. brazosensis 4 0 0 0 0 fo) 0 .02
N.potteri ho 10 0 10 17 1 0 78 39
N. bairdi 635 323 3 2505 908 388 5 4767 23.83
N. lutrensis 2285 511 3 3 320 205 83 3410 17.06
N. buchanani 106 3 0 0 0 ° 0 109 54
Hybognathus 1335 157 0 393 2503 581 88 5057 25.28
P. vigilax 8 3 fe) 6) fe) ) re) 7. 05
P. promelas 11 13 0 0 3 16 25 68 34
I. punctatus 10 6) 6) 0 O 8) 6) 10 -05
I. melas 64 8 ) fe) 6 fe) 62 1ko -70
F. kansae 4 ) 0 2669 55 98 33 2859 14.29
Cyprinodon 14 k k 2591 4 223 14 2,854 14.27
Gambusia 22 36 0 + ) 0 fe) 59 .29
Micropterus 6 3) 0 fe) 1 9) ) 7 .03
L. cyanellus 30 18 fe) 2 26 18 35 129 64
L. macrochirus 14 1 ) fe) 2 2 fe) 19 09
L. humilis 60 ‘aT fe) fe) 12 fe) 3) 99 hg
L. megalotis 10 1 fe) fe) ) fo) fe) 11 -05
Pomoxis 8 0 fe) ) 1 0 ) 9 -O4
Total 4.825 1199 10 8180 3914 1532 345 20,005 99.97
% of Total 2k .12 6.0 0 (+) 40.9 19.6 TT 137 100.00
--- Page 22 ---
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--- Page 23 ---
Treated sewage effluent from the city of Vernon. This
water is well treated, free of all solids and clear.
--- Page 24 ---
West Vernon Station under normal conditions.
--- Page 25 ---
North Fork Station. River is usually dry here, and
collections were taken from isolated pools below cliffs
on the left.
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