(1962) Job Completion Report: Statewide Rough Fish Control, Job No. 16a39, A Chemical Treatment to Reduce Existing Fish in the Concho River Watershed above Twin Buttes Project
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JOB COMPLETION REPORT
As required by
FEDERAL AID IN FISHERIES RESTORATION ACT
TEXAS
Federal Aid Project No. F-14-D-6
STATEWIDE ROUGH FISH CONTROL
Job No. 162839 A Chemical Treatment to Reduce Existing Fish in the
Concho River Watershed Above Twin Buttes Project
Project Leader: Lawrence S. Campbell
H. D. Dodgen
Executive Secretary
Texas Game and Fish Commission
Austin, Texas
Marion Toole Eugene A. Walker
D-J Coordinator Director, Program Planning
December 3, 1962
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ABSTRACT
Approximately 151 miles, comprising 95.7 per cent of all major stream areas
of the Concho River System located above Twin Buttes Project, were treated with
fish toxicants to reduce existing fish life. Many pot holes,located in secondary
tributaries, and eight watershed stock tanks were treated. To avoid unwarranted
destruction of endemic species, headwater springs and several other spring areas
were not treated, These areas were partially cleared of problematic species by
seining and gill netting. Toxaphene was used to treat 3,942 acre feet of water.
This chemical was only used where flow was negligible and where stream water was
not used for human consumption. Powdered rotenone was used to treat 1,834 acre
feet of water where flow was pertinent or where the stream was a human water
supply. Much of the stream was treated by workers walking in the stream bed and
spraying the toxicant from small units placed upon the workers’ backs. Larger pools,
such as those created by dams, were treated by medium sized units mounted in boats.
The lake treating unit developed under project F-7-R was used to treat the two
largest pools of the South Concho River. A total of 328 persons was contacted
to obtain ingress to difficult-to-reach stream areas and to secure permission
to treat private but associated waters. Pretreatment salvage operations captured
1,200 game fish of species not presently available from hatcheries. These fish
were returned to various stream areas as part of the post treatment restocking.
Post treatment evaluations indicate that existing fish populations were reduced
by more than 95 per cent, and that undesirable fish were reduced to less than 1
per cent of their former weight and number. Restocking has been completed
insofar as present limitations will permit. Over 111,000 game fish and 250,000
native forage minnows have been released. This timely development effort on
8,000 acre feet of water should greatly enhance the productivity of Twin Buttes
project, and extend the period of good sports fishing after the reservoir reaches
a capacity of 170,000 acre feet.
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JOB COMPLETION REPORT
State of Texas
Project No. F-14-D-6 Name: Statewide Rough Fish Control
Job No. 16a39 Title: A Chemical Treatment to Reduce Existing Fish
in the Concho River Watershed above Twin
Buttes Project
Period Covered August 1, 1962 - September 31, 1962
Objectives:
To drastically reduce existing fish in the above waters prior to impounding
sizable quantities of water in Twin Buttes Reservoir.
Methods and Specifications:
1.
Approximately 151 miles, comprising 95.7 per cent of all major stream
areas of the Concho River System located above Twin Buttes Project,
were treated with fish toxicants to reduce existing fish life.
Chemical applications were completed between July 24, 1962 and
September 31, 1962. Stream areas treated include the following:
(1)
(2)
(3)
(4)
All waters in the primary stream bed of the Middle Concho River
from Twin Buttes Dam to the western limit of the Bar S Ranch,
an estimated 62 miles of stream.
All waters of Spring Creek from its confluence with the Middle
Concho River to a point 1 1/2 miles below the headwater springs
located on the Reginald Atkinson Ranch, an estimated 37 1/2 miles
of stream.
Waters of Dove Creek located between a point one-fourth mile above
the area where water is backed up by Guinn Dam to Knickerbocker
Crossing and all waters of Dove Creek located below the most
eastward dam on XQZ Ranch to the confluence with Spring Creek, an
estimated 16 miles of stream.
All waters, excepting some springs, of the South Concho River
located below Ford Boulware Ranch and the diversion dam on the
South Concho River, a stream distance of 24 miles.
In addition to the above specified waters, many pot holes located in
secondary tributaries, and eight stock tanks were ehemically treated.
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To avoid unwarranted destruction of endemic species, headwater springs
and other spring areas were not chemically treated. However, these
areas were partially cleared of problematic species by seining and gill
netting. Untreated areas comprised approximately 6 1/2 miles or 4.3
per cent of the total stream areas involved.
Selection of toxicants used was determined by circumstances that prevailed
in particular stream areas. In order to minimize costs, toxaphene was
used in all waters where stream flow was negligible and where the waters
were unassociated with public drinking water. Virtually all of the Middle
Concho River and Spring Creek were treated with toxaphene, as well as
all pot holes and stock tanks. Six hundred fifty seven gallons of 6 pound
toxaphene were used. The total volume of water treated with toxaphene
was estimated at 3,942 acre feet. The dosage calculated for specific
areas was never less than .19 parts per million. Powdered rotenone
was used in areas where stream flow was pertinent and where the stream
was a source of water for human consumption. It was also necessary to
use powdered rotenone for all work done after August 24, 1962, so that
more rapid detoxification would occur to permit restocking of the waters
in the fall of 1962. The rotenone used varied in toxicity from Prentiss
60W, having an equivalent of 20 per cent active ingredients, to more
commonly used powders, having 5.67 and 6.71 per cent active ingredients.
The equivalent of 5,500 pounds of 5 per cent powdered rotenone was used
to treat 1,834 acre feet of water. All areas previously described for
Dove Creek and South Concho River were treated with rotenone, and the
calculated dosage for specific areas was always greater than 2 parts per
million.
The means of application of toxicant varied according to circumstances.
Where minor quantities of water extended for significant distances, the
stream was treated by personnel walking in the stream bed and spraying
the toxicant into the water by means of small manually-operated sprayers.
These small capacity units were strapped to the backs of the workers.
In larger pools, such as those created by low water impoundments, the
areas were treated by medium capacity units mounted in boats. These
units controlled the release of chemical by means of globe valves,
functioning through siphoning action and employing the action of out-
board motor propellers to aid in dispersal. The largest pools of the
South Concho River, the pools at Christoval County Park and above
Gardner Dam, were treated by the lake treating unit developed under
project F-7-R.
Three hundred twenty eight persons were contacted to obtain access to
difficult-to-reach stream areas and to secure permission to treat private
but associated waters. Local and national authorities concerned with
the project were contacted to inform them of the work proposed and to
secure their cooperation.
Limited salvaging operations were also included. This work was under-
taken in order to secure brood fish of several game species that are
not presently available from state fish hatcheries.
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8, Limited evaluation procedures were also included. However, the urgency
of completing the work before flooding could occur did not permit
extensive evaluation of the work while it was in progress.
Results:
Results of the treatment confirmed sampling data obtained from the pre-
impoundment survey, and indicated that previous evaluation of the fishery problem
may have been conservative. Many tons of undesirable and problematic fish were
destroyed and relatively few desirable game fish.
Total existing fish populations were drastically reduced, probably by more than
95 per cent, and undesired or problematic fish were reduced to less than 1 per
cent of their former weight and number. In untreated areas game fish ratios were
higher than was common for the watersheds.
Discussion:
At this time there is every reason to be optimistic about the gross success
of the management work. Pools being created by the dams are expanding. Over
2,000 acre feet of water are impounded by the South Concho Dam, and approximately
1,500 acre feet are contained in the Middle-Concho-Spring Creek Basin. This
increase is expected to continue. The spring fed tributaries increase in flow
during the winter months and there is less withdrawal for irrigation. Even if
run-off does not occur the combined structures should impound over 12,000 acre
feet of water before May 1963. If the normal spring flooding occurs at that
time over 40,000 acre feet of water should be impounded within the next six months.
Seining and observations have also indicated that the control effort was highly
successful. By exercising timely management in waters whose total volume was
less than 8,000 acre feet, a temporary control has been effected upon problematic
fish populations that would ultimately have adversely affected game fish produced
in waters totaling 170,000 acre feet.
Restocking of all watersheds has been completed insofar as the present
limitations will permit. A total of 111,700 game fish made up of 40,000
largemouth bass fingerlings (Micropterus salmoides), 30,000 redear sunfish
(Lepomis microlophus), 30,000 channel catfish (Ictalurus punctatus), 8,000
blue catfish (1. furcatus), 2,500 flathead catfish (Pylodictus olivaris), and
1,200 adult native sunfish salvaged through pretreatment effort have been
distributed in the cleared areas of the stream. In addition to these fish over
250,000 native minnows have been trapped and released.
Estimated Costs:
A. Salaries and Wages
Leader, 30 days @ $26.05 per day $ 781.00
Fisheries Technician, 20 days @ $14.55 per day 291.00
Field Assistants (4), 80 days @ $13.55 per day 1,084.00
$ 2,156.00
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side
B. Traveling Expenses
Mileage - 3,000 miles @ $ .08 per mile $240.00
$ 240.00
C. Operation of Equipment
Gas, oil, lubricants, etc. $ 75.00
$ 75,00
D. Materials and Supplies
1, 657 gallons of 6 pound toxaphene
@ $2.20 per gallon $ 1,445.00
2. Equivalent of 5,500 lbs. of 5% powdered
rotenone @ $ .31 per 1b. 1,705.00
$ 3,150.00
Total Costs $ 5,621.00
Recommendations:
Studies should be made to evaluate the results of this work in order to
provide a logical basis for determining when the reservoirs should be opened
for fishing.
Prepared by _Lawrence S. Campbell Approved by LL enteen Goole
Project Leader Coordinator
Date December 3, 1962 Leo D. Lewis
Regional Supervisor