TPWD 1967 F-4-R-14 #1158: Fisheries Investigations and Surveys of the Waters of Region 2-A: Job No. 3-36, Evaluation of the Pre-impoundment Rotenone Treatment of Hubbard Creek Lake
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Marion Toole
D-J Coordinator
JOB COMPLETION REPORT
As required by
FEDERAL AID IN FISHERIES RESTORATION ACT
TEXAS
Federal Aid Project No. F-4-R-l4
FISHERIES INVESTIGATIONS AND SURVEYS OF THE WATERS OF REGION 2-A
Job No. 3-36: Evaluation of the Pre-impoundment Rotenone
Treatment of Hubbard Creek Lake
Project Leader: Charles T. Menn
J. R. Singleton
Executive Director
Texas Parks and Wildlife Department
Austin, Texas
Eugene Aa Walker
Director, Wildlife Services
December 15, 1967
Abstract
The pre-impoundment rotenone treatment performed on Hubbard Creek Reservoir was
not effective and failed to be of any advantage to the "game species” pOpulation in
that lake.
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Job Completion Report
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Objective:
This study was conducted in an effort to evaluate the effectiveness of reservoir
preuimpoundment rotenone treatments. The lakes involved in this study were Proctor
Lake and Hubbard Creek Lake.
Techniques Used:
Fortymtwo farm ponds and sloughs in the basin of the Hubbard Creek Lake were
treated with rotenone at the rate of 1.5 ppm. Hubbard and Sandy Creeks were also
treated at the same rate. These steps were taken in order to eliminate the existing
fish populations in the basin area. (Project Ful4-DU6, Job l6a37). There was no pre-
impoundment fish kill treatment performed on Proctor Lake.
Description of Lakes:
Hubbard Creek Lake
Hubbard Creek Lake is located about 6 miles northwest of Breckenridge, Stephens
County, Texas. It was built by the City of Abilene and is controlled by the West
Central Texas Municipal Water District. The earthen dam, across Hubbard Creek below
the confluence with Sandy Creek, impounds 163000 surface acres of water. The primary
purpose of the lake is to supply water to Abilene and smaller surrounding cities.
No efforts were made to provide recreational facilities. Construction was completed
in the fall of 1962 and 23000 surface acres of water were impounded that year.
Soils on the watershed are primarily of clay-loam with underlying limestone.
Shoreline vegetation is limited. Mesquite is the predominant tree while the shores
line supports bermuda grass, sunflowers and various range grasses and weeds.
Proctor Lake
Proctor Lake is located in the Brazos River Basin in Comanche County3 9 miles
northeast of Comanche on the Leon River3 a tributary to the Brazos River. The dam was
built by the U. S. Army Corps of Engineers for flood control and water conservation.
Work on the dam was completed in the spring of 1963. Due to heavy rains on the
watershed the lake was filled immediately.
-2-
Lake Proctor has 4,600 surface acres of water which is supplied by Rush Creek,
Sabanna River, and Leon River. Soils on the watershed are primarily sand with
underlying clay. Peanuts and watermelons are the principle crops grown on the
immediate watershed. The shoreline has a variety of trees, but consists mostly of
large pecan trees intersPersed with post oak. Bermuda is the predominant grass.
Launching ramps, camp sites, picnic areas and paved roads, built by the Corps
of Engineers make the lake very attractive and extremely accessible to the public.
Stocking of Lakes
After eradication was completed on Hubbard Creek Reservoir, heavy rains inundated
2,000 acres of fertile pasture land. The lake was stocked with 150,000 channel catw
fish, 37,000 blue catfish and 10,000 bass fingerlings. This stocking took place the
last week of August. Subsequent stockings of both Proctor and Hubbard Creek Lakes
are tabulated in Table 1.
Table l
Stocking of Hubbard Creek Lake & Proctor Lake
Hubbard Creek Lake
Largemouth Channel Catfish Flathead Crappie
Date Bass Catfish Blue Catfish White
8-62 10,000 2,000 ,
9-62 5,000 103,050 12,000
10-62 19,000 10,700 24,000 2,000
4-63 9.29.299 . . . .._.._...... ._., rags
Totals 384,000 115,750 36,000 2,000 1,096
Proctor Lake
Date Largemouth Channel 'Catfish Flathead Crappie
Bass Catfish Blue Catfish White
6-63 167,700
8—63 76,980
10-63 5,050
Totals 167,700 _ 76,980 5,050
m3-
Gill nets were used to sample fish populations and were set at stations established
during the initial (Fw4uR-ll) segment of this job. The nets were 150 feet long and
6 feet deep with square mesh graduated from 1 inch to 3% inches, changing every 25
feet. Nets were set in the afternoon and raised the following morning. Netting
trips were distributed more or less randomly over the segment periods. The yearly net
footages for each lake are shown in Table 2.
Table 2
Yearly Net Footages
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65-»66 ”Listings m7 genres};
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Scientific names of fish mentioned in this report are shown in a checklist
(Table 3). The checklist also categorizes the various species included in the terms
”rough fish”, “game fish” and ”miscellaneous sunfish” as used in this report.
Table 3
Checklist of Fishes Mentioned in This Report
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Table 3 (continued)
Checklist of Fishes Mentioned in This Report
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Game Fish
Channel catfish Ictalurus punctatus
Blue catfish Ictalurus furcatus
Flathead catfish Pylodictis olivaris
Largemouth bass Micropterus salmoides
White crappie Pomoxis annularis
Miscellaneous Sunfish
Warmouth Chaenobryttus gulosus
Green sunfish Lepomis cynellus
Redear sunfish Lepomis microlophus
Bluegill Lepomis macrochirus
Longear sunfish Lepomis megalotis
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It should be noted that water analyses were made on each lake at an established
station during the segments. Tests were made to determine dissolved oxygen, carbon
dioxide, pH, and alkalinity. The results of these tests showed both lakes to be
similar in water quality.
Data:
The netting data for segment 3, 1965-66, are shown in Tables 4 and 5. Netting
data from previous segments can be found in the Job B-3l completion report F-4-R~12.
Table 6 consists of the tabulated netting data for all three years in regards to per
cent of number and per cent of weight. These are also graphically illustrated (Table 7).
Table 6
Per Cent of Number and Weight
__._____________________._____a__________________i_____i___
Hubbard Creek Lake
Per Cent of Number Per Cent of Weight
1963-64 1964-65 1965-66 1963-64 1964565 1965—66
Rough Species 40.65 61.85 45.15 55.36 65.39 62.84
Game Species 35.51 32.20 34.41 41.95 34.06 35.21
Miscellaneous
Species 23.84 5.95 20.44 2.69 0.55 1.95
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Table 6 (continued)
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Proctor Lake
Per Cent of Number ' Per Cent of Weight
1963-64 1964-65 1965-66 1963-64 1964-65 1965-66
Rough Species 40.71 51.08 54.34 41.87 45.46 57.43
Game Species 54.97 42.73 37.90 57.15 53.64 _41.48
Miscellaneous
Species 4.32 6.19 7.76 0.98 0.90 1.09
W
Discussion:
To better understand the data and draw some conclusions several indices must be
chosen. Several interesting facts can be seen by comparing such factors as per cent
of numbers and per cent of weight (Tabler 6 and Figure l).
The graph comparing per cent of numbers for both lakes shows several things:
1. Although Hubbard Creek Lake received pre-impoundment rotenone treatment,
the total per cent of ”rough species” in this lake for the first year
was almost equal to the "rough species percentage" of Proctor Lake which
was not treated before stocking.
2. The per cent of ”game species” in Proctor Lake was greater than the
percentage in Hubbard Lake during the first year. However, it must be
noted that the per cent of "miscellaneous species" for the first segment
were greater in the treated lake, Hubbard.-“
Numbers 1 and 2 seem to indicate that the pre-impoundment rotenone treatment had
little or no influence on the fish populations in Hubbard Creek.
r.
W
1/
If a rough fish - game fish comparison is used to determine effectiveness of
pre-impoundment rotenone treatments, the role of the ”miscellaneous Species” cannot
be overlooked. It must be realized that there is a possibility that the ”miscellaneous
fish” may occupy part of the habitat of either the game or the rough p0pulation.
Since the”miscellaneous species“ could influence either population, it is assumed
that their affect will not greatly bias this study.