(1968–1969) Job Progress Report: Life History Study of the Flathead Catfish (Pylodictus olivaris), Federal Aid Project No. F-9-R-17, Fisheries Investigations - Region 5-A
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JOB PROGRESS REPORT } fr. }
As required by
FEDERAL AID IN FISHERIES RESTORATION ACT
TEXAS
Federal Aid Project No. F-9-R-17
FISHERIES INVESTIGATIONS - REGION 5-A
Job No. IV Life History Study of the Flathead
Catfish (Pylodictus olivaris) ©
Project Leader: K. W. Gholson
J. R. Singleton
Executive Director
Parks and Wildlife Department
Austin, Texas
Marion Toole Eugene A. Walker
D-J Coordinator ; Director, Wildlife Services
March 19, 1970
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SUMMARY
Field work was continued on the Medina and Rio Grande watersheds. The
most efficient collection tools were found to be the telephone generator
and large mesh gill nets. After a period of three months, one of
every
three fish caught in a four-inch bar mesh gill net was a tagged fish, thereby
illustrating how effective gill nets would be in drastically reducing the
flathead population.
Stomach analyses were completed on over 800 young-of~the-year
flatheads, and 600 adult fish were tagged and released in the two
The growth rate of young fish is approximately 9 mm per month
12-month period.
There has not been sufficient data gathered to make any valid
pertaining to movement patterns of reproduction,
The distribution of Pylodictus olivaris on the North American
is included in the text and shown by map.
and juvenile
watersheds.
over a
assumptions
continent
A bibliography of published and unpublished reports is also included
herewith.
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JOB PROGRESS REPORT
State Texas
Project No.; _F-9-R-17 Project Title: Fisheries Investigations -
. Region 5-A
Job No.: IV Job Title: Life History Study of the
Flathead Gatfish (Pylodictus
olivaris) _
Period Covered: December 1, 1968 to November 30, 1969 _
Background:
The need for an efficient predator to control forage and overproductive
game fishes in streams and lakes has long been recognized as one of the most
pressing problems in fisheries management. Numerous fisheries investigators
have conducted limited research with the flathead catfish, stocked alone and
in combination with other fish species. However, this research has been
restricted by the fact that adequate numbers of stocking-sized catfish of
known age have not been available.
Because fisheries personnel have recognized this need for large numbers
of various sized flathead catfish of known ages, many attempts have been made
to propagate this species.
Disease, cannibalism, failure of fry to accept food, and other yet un-
known factors have greatly hindered the success of these endeavors.
Because of its possible value as a tool in fisheries management, and
its value as a food and sports fish, and the difficulties encountered in the
propagation of this species, it seemed necessary to conduct a life history
study of the flathead catfish. This study was designed to investigate and
research this fish in its native habitat.
Two radically different watersheds were chosen as sites for the initial
phases of this study, the Rio Grande River with its highly turbid waters,
and the much smaller Medina River with its clear spring-fed waters. Both
rivers are known to support substantial flathead populations, This contrast
will provide an excellent opportunity to observe any differences in feeding
habits, spawning, growth rates, and other pertinent data.
Objectives:
During this segment, research objectives included the following:
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l. To research literature on the use of sonic and radio tracking
equipment.
2. To compile a bibliography on flathead catfish in general.
3. To determine size range and growth rates of 0-1 age class in
both river and lake habitats.
4, To determine food and habitat requirements for pre»adult flat-
heads.
5. To determine whether flatheads in connecting rivers and lakes
maintain separate and distinct populations.
6. To determine spawning locations and seasons.
7. To determine individual movement and migration patterns.
8. To determine methods of spawning and rearing flatheads in
hatchery ponds.
Procedures:
Correspondence was continued with various agencies and individuals
connected with research on the flathead catfish. A bibliography is included
in this report with the annotated bibliography to be included in the final
report.
During this segment, 803 young flatheads were collected for stomach
analyses, and 709 larger fish (200 mm+) were tagged with plastic spaghetti
tags and monel strap tags to determine movement and rate of growth (see
Table 4).
The telephone generator was used for collecting young-of-the-year and
juvenile flatheads in both the Medina and Rio Grande watersheds.
Can traps were again used in varied arrangements with negative results.
A fine mesh nylon bag (1/8" mesh) was sewn into a thirty-foot bag seine
and used in conjunction with a telephone generator on the Medina and Rio
Grande Rivers to collect post-larval flathead fry, This method also proved
inefficient. The seine was used in small, isolated areas of the Rio Grande
during rotenone collections. Again, juvenile fish were collected, but no
fry appeared.
For larger fish, the telephone generator was utilized during the warmer
months and gill nets during winter months.
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~ 10
Findings:
Previous collection methods were improved, and flatheads of all sizes
(except post-larval) were collected efficiently.
The telephone generator is ineffective in waters below 60° F.
The majority of the gill nets were 4-inch bar mesh and were extremely
successful in winter months (Table 5), As noted, this bar mesh proved
highly selective for flathead catfish from 10-70 pounds and larger cyprinids.
This size mesh will be employed extensively in the next segment along with
5-inch mesh nets.
In an effort to collect more young adult fish (1-8 pounds), 1,000 feet
of 3-inch bar mesh gill netting was employed with limited success, Many
other species of fish, including many game fish, were collected in the
3-inch nets along with a few flatheads in the desired size range. There-
fore, for time expended and specimens acquired, 3-inch nets were not suitable,
Two flatheads were taken from an illegal hoop net on the Rio Grande
River that had been placed in a narrow channel of swift-flowing water.
These fish were tagged and released at a point some distance downstream.
One of the two fish had been tagged before.
Habitat:
Adult lake fish were collected in water from 10-90 feet in depth by
gill nets, but with limited success in depths over 45 feet, Most fish were
taken near the old river channel in 15-35 feet of water The only areas
in this depth range that did not yield fish consistently were heavily
silted or were old submersed fields.
Adult lake and river fish were collected with the telephone generator
in water depths of from 4-25 feet around obstructions such as boulders,
large trees, and rock ledges. As determined in the previous segment,
adult fish were always found where some current existed, regardless of
water depth. Also, as in segment 16, young-of-the-year and 1-2 year class
fish were collected in shallow, fast-moving water over a hard rock or brush
littered bottom,
In the summer the old river channel in the upper part of Medina Lake
was approximately 18 feet deep in the center with the banks of the channel
being 7-10 feet under water. Late in the summer, heavy rains on the water-
shed raised the lake level by 12-14 feet and telephone generator collections
a few days afterward produced numerous young: of-the-year fish along the oid
river channel in 18-20 feet of water where only one such fish had been
observed during all previous collections.
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«19+
Reproduction:
Information on flathead reproduction is still vague and inconsistent.
It is apparent, in both the Rio Grande and Medina watersheds, that all
females do not develop at the same time of the year. Insufficient
numbers of spawning sized adults have been sacrificed to show any definite
spawning activity patterns. Specimens will be sacrificed in greater numbers
from the Rio Grande River during the next segment in order to gain more
knowledge of sexual development patterns. The Medina River will be ex~
cluded from this phase of data collection because of its relatively small
size. Its recruitment potential is far below that of the Rio Grande and
continued harvest of adult fish would probably produce a noticeable
change in the overall population.
In the few fish sacrificed previously, there were few mature females in
any specific size group. In the course of stomach analyses, 9 fish in the
79-235 mm (1.125% of the total) range contained ovaries with developed
eggs. Of these nine fish, taken from the Rio Grande River, eight were be-
tween 79 and 168 mm.
Work was initiated on the Medina Hatchery in an effort to spawn flat-
heads artificially. Three pairs of fish were used, and females were injected
with chorionic gonadotropin at the rate of 500 I. U. per pound of body weight.
One spawn was obtained and moved to the San Marcos Hatchery catfish
incubator. The resulting fry appeared to be deformed, did not absorb the
yolk sac, and eventually died. Water temperature at the Medina Hatchery
was 83° F. preceding and during the spawn and was probably the key factor
involved in the failure of the fry to survive.
A total of eight feral fish were transferred from Medina Lake to the
Medina Hatchery to be used in the 1970 spawning season. A number of fish
in the .5 to 2.0 pound size range from the Rio Grande were stocked in ponds
on the hatchery in 1968 for use as broodfish in the future.
Valuable information during this segment, relative to reproduction and
culture of flatheads, was obtained at the U. S. Department of Interior Fish
Farming Experimental Station, Stuttgart, Arkansas, from Kermit Sneed and
John Guidice. Their findings indicate that the combination of healthy,
hatchery-reared broodstock and the use of chorionic gonadotropin injections
is the most consistent method of inducing flatheads to spawn under hatchery
conditions,
Growth Rate:
To date, data does not show a definite growth rate of adult fish by
weight during a specified period of time. However, tagged adult fish do
exhibit an average length increase of 7.5 mm per month.
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=] 3.
Growth of young-of-the-year during the past two years averages 10.0 mm
per month for fish in the Medina River and 8.3 mm per month for Rio Grande
flatheads (Table 6a and 6b). Although Medina River fish overtook the Rio
Grande fish by November in 1968, the reverse occurred by November 1969,
The only explanation of this reversal, that can be offered at this time,
is that there is nearly six weeks difference in the fall collection times
in 1969 and the Rio Grande fish had a lead of 4 mm more in July 1969. By
adding an extra six weeks growth to the Medina fish (15 mm) and subtracting
the 4 mm gained by July from the average length of the Rio Grande fish, the
growth trend of 1969 is the same as in 1968. Considering these inconsis-
tencies, data will be collected in 1970 as it was in 1968 to substantiate
the trend.
The smallest fingerlings collected in June average 110 mm standard
length and are believed to be one year old. Assuming the spawn occurred in
June of the preceding year, they would, therefore, exhibit a growth rate of
approximately 9 mm per month over a 12-month period. This rate appears
consistent in both watersheds.
Movement Patterns:
Movement of all recaptured fish appears to be quite random both in
frequency and distance (Table 7). Of the 709 fish captured and tagged, only
22 fish were recaptured. Two of these were recaptured two times and two,
three times. The average number of days of freedom between recapture is
28.1 days. There is no correlation between period of freedom and distance
of movement,
Movement of fish in both the Medina and Rio Grande Rivers is basically
the same as that for Medina Lake. Some were recaptured two and three times
exhibiting erratic movement with no relation to period of freedom.
Twenty additional tags have been returned by fishermen and game manage~
ment officers. The weight of these fish varied from 1 to 45 pounds and
showed movements of from .25 to 4.0 miles in Medina Lake. One fish tag
returned from the Rio Grande River showed the fish moved approximately 10
miles upstream.
Although biased by a number of factors, tag returns from anglers indicate
that 65 per cent of these fish were caught within 60 days after release
(Table 8).
It is hoped that a larger number of fish can be tagged in early 1970 and
sonic instruments will be used to obtain more conclusive data on movement
patterns.
Food Studies:
A total of 823 flathead catfish stomachs were examined during this
segment. These specimens were divided into three size groups:
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--- Page 19 ---
a
Table 8
Elapsed Time Between Tagging and Recovery - Sportfishing
November 13, 1969
July 3, 1969
June 24, 1969
March 21, 1969
October 3, 1969
April 15, 1969
June 12, 1969
June 12, 1969
May 14, 1969
May 2, 1969
March 19, 1969
May 14, 1969
March 20, 1969 |
June 24, 1969
March 13, 1969 |
May 9, 1969
July 30, 1969
March 12, 1969
April 1, 1969 |
March 14, 1969
July 14, 1969
July 4, 1969
April 7, 1969
October 23, 1969
May 12, 1969
July 10, 1969
July 19, 1969
June 26, 1969
June 18, 1969
May 9, 1969
July 7, 1969
May 17, 1969
September 6, 1969
June 6, 1969
August 8, 1969
November 22, 1969
August 9, 1969
September 16, 1969
September 13, 1969
Tag Recovered _
November 18, 1969
Days Elapsed
= oi
5
TL
11
17
20
27
28
37
42
47
51
54
58
74
85
91
115
150
168
187
--- Page 20 ---
-18-
A. 9-79 mm standard length - Table 1
B. 80-199 mm standard length - Table 2
C. 200 mm standard length - Table 3
These tables substantiate the assumption drawn in the previous segment
that Medina River flatheads change to a fish diet at an earlier age than
do the Rio Grande fish. -From Table 3 it should be noted that 71.9 per cent
of the stomachs from the Rio Grande fish contained fish or fish remains
while 100 per cent of the stomachs from the Medina River contained fish
remains, Tablesl and 2 show the same trends but with some Variation in
percentages relative to Table 3. Analysis of these tables yields the fol-
lowing stomach content percentages:
Fish or Fish Remains Insects or Insect. Remains
ED ea LTS
Table j
Medina 0.8 92.1
Rio Grande 0.0 99.0
Table 2
Medina £,6 84.1
Rio Grande L2 97.1
Table 3
Medina 100.0 0.0
Rio Grande 71.9 21.9
Although many insect orders were present in these analyses, Ephemeroptera
was the preferred food,
The stomachs of the larger flathead catfish (10 pounds or greater) in-
dicate these fish feed on gizzard shad, Crappie, carp, and various sunfish
as large as is Possible to swallow, Shad removed from Stomachs range up to
200 mm, Partially digested carp that had an approximate total length of
200 mm have been found in Sill nets alongside large flatheads.
Stomach analyses will be conducted on those fish from the Rio Grande
that are to be Sacrificed for sexual development data in the next segment,
These analyses should provide more basis for conclusive feeding habits of
large adult flatheads.
Discussion of Tables:
Tables 1-3 were compiled from examinations of 823 flathead stomachs
Figures given are for percentage of occurrence,
Table 4 is a record of tagging activities for each watershed, Fish
listed were taken by either a telephone generator or gill net,
--- Page 21 ---
-19-
Table 5 illustrates the effectiveness of large-mesh gill nets in col-
lecting flatheads, Nets used were primarily 4-inch bar mesh with 3-inch
bar mesh being employed 25 per cent of the time.
Table 6a compares standard lengths of young-of-the-year collected in
July in the Medina and Rio Grande Rivers. This chart is used to determine
the average length in July for comparison with average length in November
to yield a growth rate during the prime growing period,
Table 6b is the average lengths in the fall used in conjunction with
Table 6a.
Table 7 lists information gained from fish recovery by project personnel
in an effort to determine movement trends and periods of freedom. MInsuf-
ficient fish recoveries were made to draw sound conclusion.
Table 8 is a record of tagged fish captured by fishermen and the “tag
recovered" data is occasionally an estimated time accurate to +5 days. As
noted earlier in this report 65 per cent of these returns occurred within
60 days after release. Most tag returns were from Medina Lake. The tagging
operation was concentrated in a part of the lake where the most trotline
fishing is encountered. Also, most fish tagged in Medina Lake were at a
time just prior to the peak trotline fishing period. Therefore, the only
valid conclusion to be drawn is that handling the fish did not have an
adverse effect on feeding habits or movement.
Distribution on the North American Continent;
Although it was not included in the original job description, corre-
spondence with virtually every state agency yielded complete distribution
information on Pylodictus olivaris, and is included herewith.
The flathead catfish is found (and native to) the Gulf Coast from
Texas, across to the western two-thirds of Alabama, then northeastward
through the northwest corner of Georgia, western fringes of North Carolina
and Virginia, through most of West Virginia to the southwest corner of
Pennsylvania. Its northemrange extends westward through Ohio, southern
Michigan, Indiana, Illinois, southern part of Wisconsin, southeast corner
of Minnesota, Lowa, up through central South Dakota to its northernmost
range in the Bismark area of North Dakota, It extends southward through
Nebraska, Kansas, Oklahoma, and westward through most of New Mexico. It
then ranges south into Mexico (but east of the Continental Divide down to
the 18th Parallel). Its southernmost range is believed to be the Rio Balsas,
(Personal correspondence, May 1969, Amin Zarur Menez, Biologist, El Director
Del Instituto Nacional De Investigeciones Biologico Pesqueras.)
In addition to its native range, the flathead has been introduced in
other areas. Those introductions are as follows:
--- Page 22 ---
~20-
Florida: 1965 Lake Beulah (in south Florida) - 1 specimen captured
1969.
South Carolina: 1965 Santee-Cooper Reservoirs and Hartwell Lake -
results unknown.
Colorado: 1958 Adobe Creek and Bonny Dam Reservoirs - believed un-
successful (personal correspondence 1969, R. A. Jones, Director of Game,
Fish, and Parks, State of Colorado).
Idaho: Early 1940's Snake River - apparently producing.
Oregon: Snake River - apparently reproducing.
Washington: Not recorded but may have moved downstream in Snake River.
Arizona: 1962 Colorado River, also San Carlos Reservoir on Gila River.
Responding well. Reproducing populations established.
California: Imperial County, All American Canal system. Recruited
from Arizona introductions in Colorado River. Established population.
\ fr |
Prepared by K. W. Gholson Approved by WZ ep viz A Ot ( a
Project Leader - Coordinator
Date March 19, 1970 Elgin M. C. Dietz
Inland Supervisor
--- Page 23 ---
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--- Page 24 ---
2276
Pylodictus olivaris Bibliography
Barnikol, Paul G. and William C. Starrett. 1951. Commercial and Sport Fishes
of the Mississippi River Between Caruthersville, Missouri, and Dubuque,
Iowa. Bulletin of the Illinois Natural History Survey.
Beckman, William C. 1952. Guide to the Fishes of Colorado. Boulder,
Colorado,
Bottroff, Lawrence, James A. St. Amant, and Wayne Parker. 1969. Addition of
Pylodictus olivaris to the California Fauna. California Department of
Fish and Game.
Breukelman, John. 1947. What Have I Caught? Forestry, Fish and Game
Commission, Pratt, Kansas.
Brown, Bradford and J. S. Dendy. Observations on the Food Habit of the Flat-
head and Blue Catfish in Alabama.
Brown, William H. 1960. The Fresh-Water Catfishes of Texas and How to
Know Them. Texas Game and Fish Commission, Austin, Texas.
Brynildson, Clifford, Arthur Ensigh, and John Truog. 1959. A Progress
Report on the Wisconsin River Catfish Survey. Wisconsin Conservation
Department, Fish Management Division.
Calovich, F. E. and B. A. Branson. 1964. The Supraethmoid-Ethmoid Complex
in the American Catfishes, Ictalurus and Pylodictis. Published in the
American Midland Naturalist.
Carroll, Billy B. and Gordon E. Hall. 1964. Growth of Catfishes in Norris
Reservoir, Tennessee, TVA, Norris, Tennessee. Journal of the Tennessee
Academy of Science, Vol. 39, No. 3.
Carroll, Billy B., Gordon E. Hall, and Robert D. Bishop. 1963. Three
Seasons of Rough Fish Removal at Norris Reservoir, Tennessee. Reprint
from Transactions of the American Fisheries Society, Vol. 92, No. 4.
Clemens, Howard P. and Kermit E. Sneed. 1962. Bioassay and Use of Pituitary
Materials to Spawn Warm-Water Fishes. Research Report 61, U. S. Fish
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Clemens, Howard P. 1954. Pre-Impoundment Studies of the Summer Food of
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Twenty-first North American Wildlife Conference.
--- Page 25 ---
“9a
Cross, Frank B. and Claude E. Hastings. 1956. Ages and Sizes of 29 Flat-
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of the Kansas Academy of Science, Vol. 59, No. lL.
Davidson, Gladney. Drum Fishing for Blue Catfish and Flathead Catfish.
Louisiana Wild Life and Fisheries Commission,
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Research Foundation, Toronto, Ontario.
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Missouri.
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and Growth. Bureau of Sport Fisheries and Wildlife. Fish Farming
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Funk, John L. 1957. Relative Efficiency and Selectivity of Gear Used in
the Study of Fish Populations in Missouri Streams. Special Technical
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Agricultural Experiment Station, Auburn, Alabama,
--- Page 26 ---
“Dk -
Hambric, Robert N. 1967. Growth Rate of Channel Catfish Fingerlings Fed
Low Protein Food Versus Growth Rate of Fingerlings Fed High Protein
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Hasler, Arthur D. and H. Francis Henderson. 1963, Instrumentation Problems
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--- Page 27 ---
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the Missouri River, Nebraska, with Emphasis on Food Habits and Growth
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--- Page 28 ---
-26-
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--- Page 29 ---
~27-
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