(1967–1968) Segment Completion Report: Region I-D Fisheries Studies, Job No. 2 Pollution Studies
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SEGMENT COMPLETION REPORT
STATE OF Texas
PROJECI NO, F-18-R~3 _ NAME _Kegion I-D Fisheries Studies
JOB NO. 2 TLiTLe Follution 5tudies
—s a a a cS sae
PERIOD COVERED ____s«sMarch 1, 1967 to February 28, 1968
ai ais PN ea et ae ee
Objectives:
General.
To investigate instances of pollucion affecting specific fish populations
and to report findings to the Water Qval_ty Berard wher remedial acric:
ig -2ednd,
Specific:
ee To determine extent of damage to fish populations.
2. To trace the source of pollution.
3. To determine the nature of the pollution.
4. To delimit saline pollution and its effects on fish populations in
the Pecos River below Red Eluff Lake and above the Rio Grande.
To report instances of violation and negligence to the State Water
Pollution Control Board,
Ln
Procedures:
Pecos River
Netted or seined fish were identified in the field where possible. Names
of fish used in this report are those accepted by the American Fisheries
Society as published in their Special Publication No. 2, 1960, A List of Common
and Scientific Names of fishes From the United States and Canada, Second Edition.
A checklist of species is included as Appendix A.
Standard survey gill nets are 150 feet long when constructed. The meshes
begin at i-inch square and progress to 3.5 inches square in 25-foot sections,
Large mesh nets are 150 feet long when built and all mesh is 3.5 inches square.
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The webbing of all nets is 8 feet deep tied down to 6 feet. Nets are constructed
so that they sink when set. The lead line follows tortom contours and the floats
support the webbing like a fence, Sets are usually made perpendicular to the
shoreline in lakes and at ar angle downstream and across in rivers.
Dissolved oxygen content was checked in the field using a Kemmerer sampler
to extract samples and a Hach kit to make the determinations. Salinity was
also determined by both project personnel and the regional chemist, Salinities
presented in this report are those determined by the chemist
Findings:
No fish kills were reported or investigated in 1967,
Bicassays
All bioassay work was done by Regional Chemist Kenneth Krueger. The
first bioassay was done using water from the 16-Mile Lake north of Pecos
(Figure 1). The bioassays were conducted using ©~gailon glass jugs. Aeration
was provided using a compressor with tubing and air stones, Twelve largemouth
bass fry, 15mm in overall length and weighing approximately 0.1 gm., were used
in the tests. The fish were fed Daphnia sp. At the conclusion of the experi-
ment (duration over 30 days}, 5 of the original 12-largemouth bass were surviving
{it was concluded that water of the quality at 16-Mile Lake in April 1967 (A in
Figures 2A and 3) was suitable fer the survival and growtn of largemouth bass
fry.
Bioassay of water from the Blue Ranch (just above Farm Road 17/76, survey
site 2 on Figure 1) was positive. Largemouth bass fry survived and grew. The
Blue Ranch is the area farthest downstream from Red Bluff which is affected
by irrigation releases.
Water taken from the "pump hole" collecting site produced only negative
results (D on Figures 2A and 3). All fry died or were very weakened within
48 hours, A 50 per cent dilution of water from the pump hole sample was made.
Survival in the 50 per cent solution was 109 per cent until the fourth day when
all fish died. There was no malfunction of equipment indicated, No other
bioassays were done.
Fish Population
The Pecos River was surveyed with gill nets and seines at 8 sites for this
job. The occurrence of species and the percentage composition for larger
(nettable) species of fish is showa in Table 1, The other species iisted are
small salt-tolerant species which were seined. Game fish are underlined in
Table 1 to emphasize areas of occurrence or absence.
Large fish taken from the Pecos River from just below Farm Road 1776
to just above Sheffield (Figure 1) were longnose gar, gizzard shad, carp, and
Rio Grande perch.
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Figure 1
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PECOS RIVER
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Sheffield
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Pecos River pH, 1967
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South of McCamey FM 30
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Figure 2B
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Pecos River pH, 1967
BYGENE DIETIGEN CO.
Southeast of Sheffield U.S. 290 as
Independence Greek Texas 349. -|.~
. Pecos R, U.S. 90
Devil's R. U.S. $0
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Water Quality
Dissolved oxygen was adequate in ali waters sampled {above 5 ppm) The
fluctuations in water quality seen in Figures 2A, 25 and 3 are probably the
result of dilution by rainwater Tetal monthiy rainfall figures are listed
in Table 2. Comparison of this table with the data in Figures 2A, 25 and 3
will reveal a close coordination between rainfall and water quality
Table 2
Total Monthiy Rainfall at Various Sties on the Pecos River Watershed in Inches
Jan. Feb. Mar. Aprii May Jone July Asg S-pt Oct Nov.
Mentone 0.00 0.00 0,00 0.00 0.00 0.71 0.56 0.00 0.40 0.00 0.58
Pecos 0.00 0.00 0.57 6.96 0.31 1.20 065 0.02 1,70 tr 0.44
Grandfalls 0.00 tr 0.02 0.38 0,00 2.01 0.89 004 0.65 010 0.42
Imperial 0.00 0.00 0.23 6.10 0.52 2.49 0.79 0.22 2.52 0,20 0.00
McCamey 0,00 0.19 0.35 9.40 0.00 0.49 0.06 1,33 270 0.15 0.60
Girvin 0.00 0.12 0.54 0,05 0,00 0.87 0.26 0.44 3.95 0.24 0.00
Sheffield 0.00 0.60 1.14 2.34 0.00 0.33 0.35 1.61 1.78 0.08 0.92
Red Bluff 0.00 0.02 0,22 0.26 0.57 1.60 1.49 0.25 0.98 ctr 0.50
Total C,00 0.5 9 70
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The pH varied between extremes of 9.1 at U.S. Highway 67 west of McCamey and
7.0 at Texas Highway 18 near Grandfalls (Figure 2A). Chlorides varied from
8,000 milligrams per liter (mg/l) near McCamey on W.U. Highway 67 to 1,000
mg/l at U.S. Highway 80 east of Pecos (Figure 3). The significance of these
tables is in the extreme variation in water quality shown. Other dissolved
solids varied just as widely and this variation has proved fatal to most
species of fish in this area as shown by surveys. Tables 3 through 6 contain
detailed analysis of water quality at all stations.
Discussion and Conclusions
Largemouth bass and channel catfish were stocked in the 16-Mile Lake
following the bioassays, Their survival and growth were excellent. The
Pecos River above Farm Road 1776 to the Red Eluff Dam is suitable for game
fish when irrigation releases maintain water ef sufficiently good quality
Red Bluff Lake filled in August 1966 and water quality was excellent for a
while. Water quality is becoming poorer as the lake is Lowered, When Red
Bluff water quality degrades because of drought, the river water quality
declines alsc, Surveys of 16-Mile Lake will be done in the spring of 1968
preceding resumption of irrigation releases in order to evaluate survival of
stocked game fish over the winter, No or few irrigation releases are made
after September, Sometimes releases are made during the winter from deep-water
strata in Red Bluff Reservoir in an attempt to impreve the quality of water
in the reservoir and provide space to accommodate any beneficial rainwater.
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The Pecos River below Sheffield is suitable for survival of game fish,
The water in the Pecos River south of Farm Road 1776 and north of Sheffield
is unsuitable for survival of game fish.
Acknowledgements
Field work and compilation of tables and figures were accomplished with
the able assistance of Technicians Charles Roberts and Joe Vasquéz. Assistance
in editing was given by Assistant Project Leader, Ronald R. Anderson,
Recommendations
No fish should be stocked in the area between Farm Road 1776 and just
above Sheffield. Efforts should be directed toward improving the quality of
water in the entire Pecos River, whenever the opportunity arises,
\
Ya plan
Prepared by George G. Henderson, Jr. Approved by Bapcove A
Project Leader Coordinator
Leo D. Lewis
Inland Fisheries Supervisor
Date March 18, 1968
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COMMON NAME
Longnose gar
Gizzard. shad
Mexican tetra
River carpsucker
Gray redhorse
Carp
Blacktail shiner
Red shiner
Proserpine shiner
Sand shiner
Roundnose minnow
Bullhead minnow
Channel catfish
Flathead catfish
Rainwater killifish
Rio Grande killifish
Plains killifish
Pecos River pupfish
Mosquitofish
Tidewater silverside
Largemouth bass
Green sunfish
Bluegill
Longear sunfish
Rio Grande perch
-]?-
Appendix A
Checklist of Species
SCIENTIFIC NAME
Lepisosteus osseus
Dorosoma cepedianum
Astyanax mexicanus
Carpiodes carpio
Moxostoma congestum
Cyprinus carpio
Notropis venustus
Notropis lutrensis
Notropis proserpinus
Notropis stramineus
Dionda episcopa
Pimephales vigilax
Ictalurus punctatus
Pylodictis olivaris
Lucania parva
Fundulus zebrinus
Fundulus kansae
Cyprinodon sp.
Gambusia sp.
Micropterus salmoides
Lepomis cyanellus
Lepomis macrochirus
Lepomis megalotis
Cichlasoma cyanogutattum