(1962–1963) Fisheries Investigations and Surveys of the Waters of Region 3-B: Experimental Use of Copper Sulphate in Killing Undesirable Fish Species, Segment Completion Report
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SEGMENT COMPLETION REPORT
As required by
FEDERAL AID IN FISHERIES RESTORATION ACT
Federal Aid Project No, F-3-R-10
Fisheries Investigations and Surveys of the Waters of Region 3-B
Job No. E-l Experimental Use of Copper Sulphate in
Killing Undesirable Fish Species
Project Leader John N. Dorchester
H. D. Dodgen
Executive Secretary
Texas Game and Fish Commission
Austin, Texas
Marion Toole Eugene A. Walker
D-J Coordinator Director, Program Planning
June 25, 1963
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ABSTRACT
During this segment two private club lakes were treated with copper
sulphate to obtain selective fish kills. Bio-assays were conducted for
each lake prior to treatment. This chemical has proved to be efficient
in controlling bullhead catfish and chub suckers. Sunfish have a higher
tolerance for copper sulphate but the chemical greatly increases their
movements, which enables very successful netting results to be obtained
with these species after treatment.
It is recommended that this job be continued during the coming
segment in an effort to explore more fully the potential value of copper
sulphate as a fish toxicant. This can be accomplished only with ex-
tended field and laboratory studies.
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SEGMENT COMPLETION REPORT
State of Texas
Project No. F-3-R-10 Name: Fisheries Investigations and Surveys of the
Waters of Region 3-B.
Job No. E-1 Title: Experimental Use of Copper Sulphate in
Killing Undesirable Fish Species. ,
Period Covered: February 1, 1962 - January 31, 1963
Objectives:
To further evaluate copper sulphate as a fish toxicant in the waters of
eastern Texas by a combination of laboratory and field tests.
Procedures:
During this segment two private club lakes, Pine Lodge Lake near Elkhart
and 3-H Club Lake near Carthage, were treated with copper sulphate to obtain
a selective fish kill. A bio-assay was conducted in the laboratory prior to
treatment using water from the respective lake. Small catfish and sunfish
were exposed to various concentrations of copper sulphate in an effort to
determine what concentration of the chemical would prove toxic to each par-
ticular species. It was also important to determine if any variation in
the water quality of one lake compared to another would cause the toxic con-
centration of the chemical would prove toxic to each particular species. It
was also important to determine if any variation in the water quality of one
lake compared to another would cause the toxic concentration of the chemical
to be varied.
Both of the lakes were netted before and after the copper sulphate
treatments. This, of course, would indicate whether or not the expected
numbers of undesirable fish had been killed.
Techniques Used:
History
Pine Lodge Lake is located 11 miles south of Palestine, near Elkhart
in Anderson County. It contains 42.9 surface acres and 240 acre feet of
water. Maximum depth is 20 feet and the average depth is about 6 feet.
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The lake was renovated in 1952 with rotenone and restocked in 1953 with
30,000 largemouth bass (Micropterus salmoides), 2,000 black crappie
(Pomoxis nigromaculatus) and 2,000 channel catfish (Ictalurus punctatus).
During the past few years however, fishing has been very poor. Biologist
C. R. Inman surveyed the lake in May 1961 and found it to be overpopulated
with sunfish and bullhead catfish.
The 3-H Club Lake is located ten miles west of Carthage, in Panola
County. The lake contains 27 surface acres and 220 acre feet of water.
The lake was completely renovated in 1956. Ten tons of limestone was
added in 1960 and submerged plants were treated that year also. In March
1961, 5,000 pounds of commercial fertilizer (10-20-10) was applied. The
fishing has been poor in this lake also for the past few years.
A netting survey by Biologist Inman in December 1961, indicated
that this lake was also overpopulated with bluegill sunfish (Lepomis
macrochirus) and bullhead catfish (Ictalurus sp.). These species
accounted for 67.97 per cent of the total netting catch. The data
contained in both lake histories was taken from Mr. Inman's reports.
Bio- assays
Prior to the treatment of both Pine Lodge Lake and 3-H Club Lake ,
a bio-assay was run. Water was hauled from the lake on which the treat-
ment was pending. Twelve 5-gallon wide mouth jars were used in the test,
Sixteen liters of water was placed in each jar and aerated by means of
an air stone in each jar. One of the jars served as a control jar and
it contained no chemical. The eleven remaining jars contained concen-
trations of copper sulphate beginning with 1.0 parts per million and
increasing 0.2 p.p.m. for each jar. Thus a range of 1.0 to 3.0 p.p.m.
was obtained. Two small catfish and two small sunfish were placed in
each jar. An effort was made to keep the size of the fish uniform but
this was not entirely possible. A time check was made approximately
every 15 hours at which time all dead fish were recorded.
Netting Methods
All pre-treatment and post-treatment netting was conducted with
experimental type gill nets 125 feet in length. The mesh size changes
every 25 feet, and ranges in diameter from l-, 1}-, 2-, 2%- and 3 inches.
Eight of these nets were set in both lakes mentioned in this report.
The pre-treatment netting was conducted the night before treatment and
the post-treatment netting was approximately one week following the
treatment.
All fish netted were weighed and counted according to species.
Coefficients of condition ("K" Factors) were calculated for some of
the game fish species.
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Method of Chemical Application
The copper sulphate was applied from an outboard boat with the aid
of a special rig which consists of a steel frame that clamps across the
width of the boat and suspends a fiberglas screened bucket in the water.
As the boat moves through the water the copper sulphate is fed into the
bucket where it is dissolved by the water as it flows through the screened
bucket. The prop-wash from the outboard motor aids in dispersing the
dissolved chemical.
Pre-Treatment Netting Results
One thousand feet of gill nets were set in Pine Lodge Lake on July 16,
1962. A total of 76 specimens was collected, 62 of these were bluegill
sunfish, bullhead catfish and chub suckers. This is 81.58 per cent by
number of undesirable species.
In 3-H Club Lake, 1,000 feet of net was also set. A total of 109
fish were caught and 103 of these were bluegill sunfish, and bullheads.
This composes 94.50 per cent of the total catch. Thesedata suggest heavy
overpopulation of these species in both lakes.
Chemical Application
On July 18, 1962, 1,300 pounds of copper sulphate was applied to
Pine Lodge Lake. This was a concentration of 1.5 p.p.m. It was originally
planned to treat this lake with a 2.4 p.p.m. concentration of the chemical,
which would have required approximately 1,800 pounds of copper sulphate.
The 1,300 pounds was on hand on the date of treatment and the remaining
500 pounds was due to arrive during treatment. However, due to a mix-up
on the order, it was never received.
The lake had been previously sounded and marked off in four sections
to enable a more even distribution of the chemical. The copper sulphate
was applied in the previously described manner from an outboard boat.
On July 19, following the treatment, numerous dead chub suckers,
yellow bullheads and bluegill sunfish were observed around the edges
of the lake. Small bass could be observed swimming, apparently unharmed
by the treatment. Also muskgrass (Chara sp.) in the lake appeared to
be dying, thus indicating the copper sulphate's value as a plant toxicant also.
3-H Club Lake was treated with 1,000 pounds of copper sulphate on
August 22, 1962. This was a concentration of approximately 2.2 p.p.m.
The lake was down about 12 inches at the time of the treatment. The
chemical was applied in the same method as in Pine Lodge Lake. Many
dead bullheads were observed after the treatment and on August 28, 1962,
when the post-treatment netting was in progress, the remains of a large
flathead catfish (Pylodictis olivaris) was observed. Table 2 gives the
water temperature of 3-H Club Lake, taken at 1l- foot intervals, on the
day of treatment.
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Post-Treatment Netting Results
Table 2 shows both the pre-netting and the post-netting results
from Pine Lodge Lake. A comparison of these two netting collections
might erroneously imply that the treatment was completely unsuccessful
due to the fact that many more bluegill sunfish and chub suckers were
netted after the treatment than before. It should be noted however,
that the copper sulphate causes great activity among sunfish populations.
Therefore, even if a considerable number of sunfish are killed by the
treatment, many more may be netted after the treatment than before due
to the greatly increased activity of the fish. This no doubt, is true
to some extent with suckers. Previous reports support this finding also.
In 3-H Club Lake, the number of sunfish netted after treatment was
again a great increase over the pre-treatment netting collection. During
the first netting, 88 bluegill sunfish were collected. After the copper
sulphate treatment, 354 of this species was netted. Results such as
these indicate that perhaps even if the chemical does not kill a really
sufficient number of sunfish, it may, with an increase in the number of
nets set, be used successfully simply by using it as an "agitator" to
move the sunfish into the nets. By using a considerable footage of small
mesh nets, the sunfish overpopulation problem in small lakes could possibly
be lessened considerably.
Table 3 contains the netting data, from both collections, on 3-H
Club Lake.
Conclusions and Recommendations:
Although all of the aspects concerning the use of copper sulphate
as a fish toxicant have not yet been fully explored, the data in this
report indicates that it is successful in controlling bullhead catfish
and suckers. Sunfish seem to have a higher tolerance to the chemical
but as mentioned, with the aid of copper sulphate sunfish can be netted
very successfully.
It is recommended that this job be continued during the coming seg~
ment in an effort to explore more adequately the full potential of copper
sulphate as a fish toxicant as well as its stimulating effects on the
movements of certain fish species. 1t can also serve a dual purpose in
some instances by controlling both undesirable fish and plants.
pe
Prepared by Joe E. Toole Approved by ZA
Asst. Project Leader “Coordinator
Date June 25, 1963 Charles E. Gra
SS 082° Eo kc
Regional Supervisor
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Table 1. Water Temperature of 3-H Club Lake
August 22, 1962
Depth (feet) Temperature (degrees F.)
) 87.5
1 87.5
2 87.8
3 87.8
4 87.8
5 87.8
6 86.5
7 86.0
8 85.8
9 84.3
10 83.0
10.5 82.0
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Table 2.
Before treatment: August 21-22, 1962
Species Number
Chub sucker 10
(Erimyzon sucetta)
Yellow bullhead 21
(Ietalurus natalis)
Largemouth bass 5
(Micropterus salmoides)
Redear 7
(Lepomis microlophus)
Bluegill 31
(Lepomis macrochirus)
Black Crappie 2
(Pomoxis nigromaculatus)
Total 76
13,
27.
Percent
16
63
6.57
40.
2.
100,
After Treatment: July 23-24, 1962
Species Number
Chub sucker 24
(Erimyzon sucetta)
Black bullhead 1
(Ictalurus melas)
Yellow bullhead 13
(Ictalurus natilis)
Largemouth bass 13
(Micropterus. salmoides)
Warmouth 2
(Chaenobryttus gulosus)
Redear 34
(Lepomis microlophus)
Bluegill 459
(Lepomis macrochirus)
Black crappie 14
(Pomoxis nigromaculatus)
Total 560
79
63
00
Percent
4.28
81
100.
.18
33
33
~35
-O7
.96
- 50
00
Netting Results of Pine Lodge Lake
Weight
4.25
12.50
8.88
0.94
2.88
30.07
Weight
10.25
0.56
21.44
35.56
83.49
Percent
14.
41.
29.
100.
Percent
Les
25.
42.
100.
13
57
53
13
- 58
05
00
28
. 68
72
68
237
»59
59
-09
00
Average
0.42
0.59
Average
0.42
0.56
0.62
1.65
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Table 3. Netting Results of 3-H Club
Before treatment: August 21-22, 1962
Species Number Percent
Blacktail redhorse 1 0.92
(Maxostoma poecilurum)
Black bullhead 5 4.59
(Ictalurus melas)
Yellow bullhead 10 9.18
(Ictalurus natalis)
Redear 3 2.75
(Lepomis microlophus)
Bluegill 88 80.73
(Lepomis macrochirus)
Black crappie 2 1.83
(Pomoxis nigromaculatus)
Total 109 100.00
After treatment: August 28-29, 1962
Species Number Percent
Largemouth bass 2 0.54
(Micropterus salmoides)
Warmouth 5 1,36
(Chaenobryttus gulosus)
Redear 3 0.82
(Lepomis michrolophus)
Bluegill 354 96.20
(Lepomis machrochirus)
Black crappie 4 1.09
(Pomoxis nigromaculatus)
Total 368 100,00
Lake
Weight
4.50
25,44
0.75
39,76
Weight
1.31
1.19
81.34
87.60
Percent
0.48
11,32
19.49
2.84
63.98
1,89
100,00
Percent
100.00
Average
0,19
0.90
0.75
0.38
0,29
0.38
Average
0.94
0. 26
0.39
0.47