TPWD 1968 F-3-R-15 #1218: FINAL REPORT: Region 3-B Fisheries Studies, Job No. B-23 Population and Reproduction Study of Channel Catfish in Lake O' the Pines, Federal Aid Project No. F-3-R-15
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FINAL REPORT
As required by
FEDERAL AID IN FISHERIES RESTORATION ACT
TEXAS
Federal Aid Project No. F-3-R-15
Region 3-B Fisheries Studies
-Job No. B-23 Population and Reproduction Study of
Channel Catfish in Lake 0' the Pines
Project Leader: Joe E. Toole
J. R. Singleton
Executive Director
Texas Parks and Wildlife Department
Austin, Texas
Marion Toole
Eugene A. Walker
D-J Coordinator
Director, Wildlife Services
May 8, 1968
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ABSTRACT
With the completion of the 1965 segment study of channel catfish (Ictalurus punctatu
in Lake 0' the Pines, it was concluded that only a limited population of adult catfish was
present. Various collection techniques including gill nets, hoop nets, trot lines and
seining failed to provide evidence of successful reproduction of channel catfish.
Extensive flooding of the reservoir during 1966 hampered efforts to determine the
effects of hydrogen sulfide gas as a detriment to channel catfish reproduction. Increases
in fish collections of 1966 may indicate an increase of channel catfish in Lake O' the
Pines. However, the fact that these fish could have entered the lake during flood stage
must be considered.
Hydrogen sulfide gas has apparently diminished in the reservoir since the flood
period as no toxic concentrations were recorded in 1967.
It is recommended that advanced fingerling channel catfish be stocked in Lake 0'
the Pines if a surplus is available. Extensive restocking is not considered feasible due
to the relative large size of Lake O' the Pines and the uncertainty of future hydrogen
sulfide levels.
It is recommended that this job be terminated with the completion of this final,
F-3-R-15 segment.
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FINAL REPORT
State of Texas
-roject No. F-3-R-15 Name: Region 3-B Fisheries Studies
Job No. B-23 ‘ Title: Population and Reproduction Study of
Channel Catfish in Lake O' the Pines
wets Narrisnh in bake YU the Pines
Period Covered: February 1, 1967 - January 31, 1968
OBJECTIVES:
To determine the need for stocking channel catfish (Ictalurus punctatus) in Lake 0'
the Pines.
1. To determine current population levels of channel catfish in Lake O' the Pines,
2. To determine if toxic concentrations of hydrogen sulfide gas are periodically
present in Lake O' the Pines.
TECHNIQUES USED;
During the 1965 and 1966 segments of this study, experimental gill nets, hoop nets,
seines and trotlines were utilized to evaluate the population level of channel catfish in
Lake O' the Pines,
Experimental gill nets: Gill nets used in this study were 150 feet in length and
eight feet in depth with mesh size ranging from 1 to 34 inches.
Hoop nets: Nylon hoop nets with mesh sizes of 2 and 2 inches Square were stretched
on cypress runners and baited with commercial dog food and cottonseed cake.
Trot lines: Nylon trot lines were constructed with 3/0 O'Shaugnessy hooks. Each
line was 100 feet’ in length with 30 hooks.
Seines: Nylon bag seines were used in an attempt to locate Spawning areas, These
seines were 26 and 16 feet in length.
Hydrogen sulfide analyses: Eight permanent sampling stations were established on the
reservoir during the 1966 segment to determine hydrogen sulfide gas levels. Early tests
were made by sodium thiosulfate-iodine titrations. Later tests were made colorimetrically
with a Hach DR-EL chemistry kit. Figure 1 is a map of Lake O' the Pines with station sites
labeled.
FINDINGS:
During the 1965 segment 50 units of experimental gill nets were set in Lake O' the
Pines. Five nets were set overnight once each month from March - December, 1965. Trot-
lines were set in conjunction with these netting activities for an approximate total of
1,800 baited hooks during the segment.
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Wilkes Reservoir
Hydrogen sulfide collection stations on Lake 0 the Pines
Figure 1.
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Six adult channel catfish were collected this segment. Four of these fish were
aught in gill nets, the remaining two on trot lines baited with small sunfish. The
baited hoop nets failed to catch any channel catfish although a few bullhead catfish
(Ictalurus_sp.) were taken.
The average weight of the 6 fish collected was 3.92 pounds, with individual weights
ranging from 2.37 to 6.37 pounds. Table 1 contains weights, standard lengths, K-factors
and sexual conditions for each catfish.
Table 1
Channel Catfish Collection Data from Lake O' the Pines - 1965
Sac nEnnnREnnereneeeenee
Standard Length Weight
Date No. (millimeter) (1b. ) K Condition
4/28/65 1 515 6.37 2.09 female-approaching
vipeness
6/29/65 2 474 3.88 1.65 female-spent
6/29/65 3 408 2.37 1.54 male-spent
6/30/65 4 390 2.37 1.77 female-spent
7/1/65 5 503 4.50 1.60 male-spent
8/30/65 6 446 4.00 2.04 female-approaching
ripeness
eee
Potential spawning areas were seined in an effort to capture fry or fingerling channel
catfish. Some areas were baited prior to seining with commercial dog food and cottonseed
cake. The Hurricane Creek area was seined most frequently because of the success cf col-
lecting adult specimens in this area. Areas were seined at varisus hours, both day and
night. No channel catfish were collected by seining.
Hydrogen sulfide tests made during the 1965 segment failed to indicate any lethal
concentrations of un-ionized hydrogen sulfide gas. The highest concentration recorded was
.06 p.p.m. from a sample taken in Johnson Creek in July. The pH value of this sample was
The results of laboratory tests under Project F-8-R-10, Job E-1, were used as cri-
teria in this study for determining lethal concentrations of hydrogen sulfide gas.
According to these findings the median lethal dosage (LD-50) of un-ionized hydrogen sul-
fide is 0.8 p.p.m. at pH 6.8, 0.7 p.p.m. from pH 7.0 to pH 7.6 and 0.6 P-p-em. at pH of
7.8 for channel catfish fry. At pH of 7.0 the LD 50 was found to be 1.0 p-ep-m. for fin-
gerling catfish, 1.3 for advanced fingerlings and 1.4 for adult channel catfish. Factor
used to compute the un-ionized hydrogen sulfide in P-pem. from total hydrogen sulfide
content was taken from Standard Methods for the Examination of Water, Sewage and Indus-
trial Wastes. These data are contained in Table 2.
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Table 2
Factors to Compute Un-ionized Hydrogen Sulfide from Total Hydrogen Sulfide Contents
nnn UE UINISnA RIA nee
pH Factor pH Factor pH Factor
Ee
5.0 0.98 6.8 0.44 7.7 0,091
5.4 0.95 6.9 0.39 7.8 0.073
5.8 0.89 7.0 0.33 7.9 0.059
6.0 0.83 7.1 0.29 8.0 0.048
6.2 0.76 Tak 0.24 8.2 0.031
6.4 0.67 7.3 0.23 8.4 0,020
6.5 0.61 7.4 0.17 8.8 0.0079
6.6 0.56 Td 0.14 9.2 0,0032
6.7 0.50 7.6 0.11 9.6 0.0013
These factors are applicable at a temperature of 25°C, For
temperatures below 20°C. or above 30°C. or for sewages having
a mineral solids content exceeding 2,000 mg/1, suitable cor-~
rections should be made.
Sewage and Industrial Wastes, page 274.
i ne ee Ens ene nade nian annenmnennmneeneneenmenmnenemanisensammesnmmenmumnemammocnencnaius mannan s ane it iii iia a ie
An additional thirty-four channel catfish were collected during the 1966 segment.
Nets and trot lines were set at monthly intervals in the reservoir with the exception of
June, when 3 collections were made. Table 3 contains collection dates, size data and
individual condition factors for each catfish taken.
Table 3
Channel Catfish Collection Data
a
Length Weight mK"
Date Number (mm. ) (grams) Factor Sex
I
2/11/66 - - - - -
3/30/66 - - - ~ -
4/25/66 dL. - 4083 - ™
5/24/66 2 255 304 1.83 male-3
6/8/66 9 522 3176 2.33 female
500 1758 1.41 male-3
396 1021 1.64 female-3
295 1539 2.10 female-5
293 404 1.61 female-5
280 412 1.88 female-3
172 82 1.61 male-3
262 314 1,76 male-3
261 305 1.71 immature
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Tabie 3 (Continued)
Length Weight "KY
Date Number Cum. ) (grams) Factor Sex
6/10/66 13 503 1.96
Z28 GA | 7”
250 362 2.3?
261. 360 2.03
226 213 2.00
225 & Lona
193 O7 ..49 re
179 iG6 4.85 femate-3
179 97 1.69 immature
102 1.66 iaje-3
6/29/66 2 101. 1.50 female-3
L219 1.94 temale-3
7/66 2 ~ - - -
8/66 ~ ~ - ~ ~
9/30/66 2 275 39% 1,88 female-5
185 90 1.42 immature
10/2/66 2 2 ~ ~ -
11/22/66 1 318 652 203. male-3
12/66 - - - - -
1/67 - - - - -
"K" Range 1.24 - 2.32
Average "K' - 1.79
Ssasnn nnn
In mid-April, 1966, the reservoir was flooded by heavy rains on the watershed. The
flood waters crested at approximately 10 vertical feet above conservation pool level.
This flooded condition presisted through June, 1966. During this period the normally
clear waters of the reservoir were throughly mixed. Figure 2 is a pheotogreph of the
flooded tailrace during flood stage. This flushing action apparently dissipated any strat-
ified concentrations of hydrogen sulfide gas. Table 4 contains hydrogen sulfide data con-
piled in 1966.
Of the 34 channel catfish collected in 1966, 24 were taken ducing the flood period
in the month of June. A total of 15 experimental gili nets and 300 baited hooks were set
during the June collections. Individual fish ranged from 82 grams in weight to 7 pounds.
Fifteen immature catfish were collected. Condition factors ranged from 1.24 to 2.32 with
the average "K" being 1.79. Figure 3 indicates size range cf the June coliection.
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Figure 2. Lake O' the Pines tailrace at flood crest
Figure 3, A portion of the June channel catfish collection -
1966
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There is a good possibility that many of the channel catfish taken in the June, 1966,
sollections entered Lake O' the Pines from Wilkes Reservoir, a private lake located on the
upper reaches of Johnson Creek. Figure 1 is a map which shows the location of Wilkes Res-
ervoir as well as the hydrogen sulfide collection stations. Wilkes Reservoir has a sub-
stantial channel catfish population and the fish could have readily entered Lake 0' the
Pines during flood stage.
@
Field work during the final segment of this study in 1967 was confined to further
hydrogen sulfide checks each month. Table 5 contains these data for all stations in 1967.
Only five analyses revealed the presence of hydrogen sulfide gas, all in sub-lethal con-
centrations.
Table 5
Lake 0' the Pines Hydrogen Sulfide Study -— 1967
Station #1 17 14 12 8 15 17 22 13 5 26
East Abutment of Dam March April May June July August Sept. Oct. Nov. Jan.
Water Temp. °F 66 73 81 83 89 84 78 70 57 43
pH 7.6 7.5 8.2 7.6 &.3 7.0 8.0 7.6 7.8 7.5
Total HoS p.p.m. - - - - - - - - - -
Unionized HS p.p.m. = = - ~ - = = = ~ -
Station #2
4Nurricane Creek
Water Temp. °F 66 73 81 83 89 82 78 70 (57 44
pH 7.6 7.5 8.1 7.8 8.4 7.7 7.2 7.6 7.5 7.3
Total HS p-p-m. a“ = ~ - - ma) - - - -
Unionized H)S p-p.m. - - - - - 027 - ~ - =
Station #3 |
Johnson Creek _ _
Water Temp. °F 68 73 81 683 88 84 78 70 ~=—58 45
pH 7.5 7.2 8.2 8.1 8.3 7.8 7.5 8.0 7.5 7.8
Total H)S p-p.m, - - “- wl - ~ ~ - -
Unionized HS p.p.m. oa “ - 004 = - “ ~ - -
Station #4 Fee
Alley Creek
Water Temp. °F 65 74 82 = 83 88 84 78 70 = 58 45
pH 7.4 7.4 8.1 8.2 8.4 7.8 8.0 8.0 8.2 7.6
Total HoS p.p.m. ~ - - “ - - - - + -
Unionized H,S p-p.m. i - = - ~ - - - - -
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Table 5 (Continued)
Station #5 17 14 12 5 15 1? 22 13 5 26
Mim's Chapel March April May June July August Sept. Nov. Dec. Jan.
Water Temp. °F 65 75 81 83 89 84 78 70 57 45
pH 7.0 7.5 8.2 8.3 8.3 7.4 702 7.8 7.8 7.7
Total HS p-p.m. oa ok = = - a“ - - = =
Unionized H5S p.p.m. - 014 # - - - - - = =
Station #6
Highway 155
Water Temp. °F 66 72 83 83 89 82 78 70 58 46
pH 703 8.0 8.1 7,2 720 7.8 7.6 6.8 7.8 dad
Total H)S p.p.m. - - - - 22 - - = ~ =
Unionized H,S p.p.m. - = 7 = 426 - ~ - - -
Station #7
Copland Creek _ ee -
Water Temp. °F 64 72 81 83 89 82 78 70 57 45
pH 8.0 7.4 123 Gad 7.0 7.7 7.2 6.8 7.8 7.7
Total HyS p.p-m. - - 22 - - ~ - - - -
Unionized H,S p.p.m. - - 04 = = = = = = -
Station #8
Brushy Creek
Water Temp. °F 65 72 81 83 90 84 78 70. 57 45
pH 7.5 8.1 8.0 8.1 38.2 7.6 7.2 8.0 7.6 7.7
Total HS p-p-m. ~ - - - _ _ - - = =
Unionized H)S p.pom. = - - - - - _ - - -
CONCLUSIONS AND RECOMMENDATIONS:
With the completion of the 1965 segment field work it was concluded that only a
limited population of aduit channel catfish was present in Lake O' the Pines. A lack of
young channel catfish in the reservoir was attributed to hydrogen sulfide gas,
The extensive flooding of the reservoir in 1966 provided an improved habitat for
channel catfish by creating homologous water conditions and dissipating existing hydrogen
sulfide gas. This improvement in water quality made difficult further evaluation of hy-
drogen sulfide effects. Apparently this flood has provided lasting benefits to the
reservoir, as 1967 hydrogen sulfide tests failed to indicate even periodical toxic con-
centrations.
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=[i=
Evaluation of the increased collection of channel. catfish obtained in 1966 is diff-
‘cult due to the possibility that these catfish may have migrated into Lake O' the Pines
auring the flood period.
Although population sampling was discontinued in 1967, several reports have been
received of good catches of channel catfish by sport and commercial fishermen. One
commercial fisherman reported taking numerous young channel catfish which indicates suc-
cessful reproduction of the species.
Additional stocking of advanced channel catfish fingerlings is recommended if a
surplus is available. It is not felt that a complete restocking of Lake O' the Pines
would be economically feasible. Without periodic flooding, hydrogen sulfide gas could
again eliminate channel catfish reproduction and prove toxic to fingerlings.
The flathead catfish (Ictalurus olivarus) may well be a factor of mitigation in
Lake O' the Pines. Numerous young flathead catfish were taken in netting activities dur-
ing this study. Increased interest in the flathead catfish is apparent from discussion
with local fishermen.
It is recommended that this job be terminated with the completion of the F-3-R-15
segment. In the event that additional stocking of channel catfish is made, future pop-
ulation and water quality data may be necessary to evaluate the stocking program.
soproved SO ectaant, Sapte.
Prepared by Joe E. Toole
Project Leader Coordinator
Date May 8, 1968 wan Charles E, Gray
Regional Supervisor