TPWD 1960 F-4-R-7 #538: A Study of Crappie in Lake Whitney
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Report of Fisheries Investigations
A Study of Crappie in Lake Whitney
Dwane Smith
Assistant Project Leader
Dingell-Johnson Project F-4-R-7, Job E-}
November 1, 1959 - October 31, 1960
H. D. Dodgen = Executive Secretary
Texas Game and Fish Commission
Austin, Texas
Marion Toole Kenneth C. Jurgens and William H. Brown
Coordinator Assistant Coordinators
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ABSTRACT
The study of crappie, Pomoxis annularis, in Lake Whitney was
continued in an effort to learn something of the size of the crappie
population, the reasons for the recent small harvest, the movement
of tagged crappie, the ecological factors influencing their distri-
bution and to develop satisfactory methods for sampling crappie fry.
Fish to be tagged were taken primarily in wire traps and by hook
and line and, beginning in July, small crappie entered the trap catch.
This seemed to indicate a successful spawn during the previous year.
Efforts to sample crappie fry during the present year's spawning
season resulted in the capture of only a single specimen in seines.
Most of the tagging occurred in the middle third of the lake,
even though traps were used in all other areas of the lake.
A total of 1,493 crappie were tagged during the year and 47,
or 3.14 percent of these were recaptured. Five crappie from previous
years' tagging were also recaptured. The greatest distances traveled
by tagged crappie were 30 miles each by two specimens, however, over half
the tagged crappie recaptured travelled less than 100 yards from the
point of release. The greatest length of freedcm for a crappie re-
caught this year was 1,030 days. This individual was recaptured
within one mile of the original point of release. Another, free for
hO5 days, was retaken within two miles of where it was released.
Since the emphasis of the study thus far has been on tagging and
recapture, and since it is indicated that tagged crappie tend to re-
main near the original point of release, it is intended that future
emphasis will be placed on the study of crappie fry and spawning
success.
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Job Completion Report
State of TEXAS
Project No. F-4-R-7 Names Fisheries Investigations and Surveys
of the Waters of Region 4-B,
Job No. E-4 Title: A Study of Crappie in Lake Whitney
Period Covered: November 1, 1959 = October 31, 1960
OBJECTIVES
To determine the population of crappie in Lake Whitney and the reasons for the
recent small harvest. To study the pattern and extent of travel of tagged or marked
crappie and the ecological factors influencing their distribution. To develop satis-
factory methods of sampling crappie fry.
PROCEDURE
The trapping of crappie, Pomoxis annularis, in Lake Whitney during the period
covered by this report continued along the same general lines as in previous segments.
Two changes, however, were the use of a gang net, in an effort to capture crappie fry,
and the use of the size three, self-piercing, strap type, monel metal tag on the
larger crappie taken in traps.
Most of the traps used were constructed of Q-gauge concrete reinforcement wire,
with a six-inch square mesh, covered with one-inch mesh poultry wire. All but one of
the traps are five feet long and 29 inches in diameter, and all are of either single-
and double-throat construction. The throat openings are from three to five inches in
diameter. The one exception is a trap constructed with a throat extending from the
top to the bottom of the trap; whereby the trap could be set in a vertical position
(Figures 1 and 2).
In addition to the described traps, three small traps were constructed with no
frame using one-inch poultry wire.
The gang net is made up of a series of hoop nets attached one to another by small
mesh leads. It was used to capture crappie fry in shallow water during the spawning .
season but was not as successful as anticipated. This was felt due to rapid water
temperature fluctuations in the shallows brought about by sudden changes in the weather.
All traps were placed at locations believed to be good crappie habitats. It was
intended that these would be permanent locations. After several collections, however,
it was decided that to catch more crappie for tagging, it would be necessary to meve
the traps from time to time.
Whenever a trap was set in a given location and the resulting take in crappie was
considered good, this trap location was used until the crappie catch diminished. If a
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location was used for a period of approximately two weeks and few crappie were taken,
the trap was moved to what was considered a better location. This procedure of moving
traps from place to place was repeated in order to capture as many crappie as possible.
Figures 1, 2, 3, and 4 illustrate the wire traps used to take crappie from Lake
Whitney. Figures 1 and 2 show an experimental trap which was constructed to catch
crappie near the thermocline. The throat, which extends vertically from top to bottom,
would extend through the thermocline.
Baiting of the traps was not practiced although one trap was baited with a cake of
pressed cotton seed meal. The trap was checked the following morning when it was found
that only 13 carp were taken. Consequently no more traps were baited. No types of
attractors were experimented with during this study period. ,
Trapping stations were established from Little Rocky Creek, near the dam, and ex~
tended to the Nolan River, near the head of the lake. This is a distance of from 20
to 30 miles of lake and river. Many of the stations used during the segment are new,
although some were used during previous segments.
The work of trapping was divided among five sections of the lake. The Brazos
River Area extends upstream from the Santa Fe Railroad Bridge (Station No. 34). What
has been called the Upper Lake Area extends downstream from the same bridge to the
vicinity of the White Bluffs (Station No. 31). The Nolan River Area lies within this
portion of the lake but the Nolan River arm extends from the lake proper. The Middle
Lake Area includes that portion of the lake from White Bluffs downstream to the Katy
Railroad Bridge (Station No. 17). The Lower Lake Area includes the remainder of the
lake, downstream to the dam.
Traps could be set in only three of the above mentioned areas at a time because
of the lack of traps. No traps were set in the Brazos River Area because the Nolan
River was utilized during this.segment. Not more than 25 traps were set an any one
given time during the study period.
The method of tagging crappie in past segments of the study was continued. Strap
type, monel=-metal, jaw tags were placed on the left premaxillary of all fish tagged.
The tag sizes used were either No. 1 or No. 3. Data recorded for each tagged specimen
were: total length in millimeters, tag number, date and place of capture and release.
Prior to release, tagged fish were cursorily examined for external parasites and for a
bacterial type of infection noted in previous study periods. None of the fish tagged
this year appeared to have this bacterial infection. .
Posters were placed in conspicuous places around the lake and newspaper articles
were published informing the public about the work being done. It was hoped that the
public would cooperate by providing information concerning any tagged fish caught.
Card forms, with blanks for the information desired, were given to camp operators on
the lake, local stores, and cafes. These cards, when properly filled out either by
individuals or by project personnel, provided needed information concerning the tagged
fish. The information received on these cards was later transferred to a ledger for a
permanent record.
Gill net collections were made in the vicinity of the wire traps to provide come
parative information concerning the relative abundance of crappie in the area. This
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also served as a check on the efficiency of the traps in taking crappie.
Common sense minnow seines and small mesh wire traps were used along the shoreline
in an attempt to sample crappie fry during and after the spawning season. In addition,
two rotenone samples were taken from restricted areas to sample crappie fry.
RESULTS
Data concerning the number of each species taken in wire traps are given along
with the percentages of the total trap catch represented by each species. The results
of trapping are presented in Table 1. The data presented covers the period from
November, 1959 through June, 1960.
The data for the months of July, August, September, and October were omitted from
Table 1 because they were inaccurately recorded by a summertime student employee. This
employee attended the traps and tagged and released all crappie taken but failed to keep
records of fish other than crappie caught in the traps. Therefore the data for the four
months were discarded.
It is interesting that white crappie, Pomoxis annularis, comprised 47.56 percent of
the total catch in traps for the eight months represented in Table 1. Bluegiils,
Lepomis macrochirus, comprised 26.43 percent. Compared to data from the previous study
period, crappie increased slightly in the catch from 44.38 to 47.56 or 3.18 percent.
Bluegills decreased from 44.78 to 26.43 or a total decrease of 18.35 percent.
There were only 47 gizzard shad, Dorosoma Wegeeeee sl comprising 3.23 percent of
the total trap catch. Yet, as shown in Table 2, 894 gizzard shad were taken in gilli
nets set near the traps. Of the total catch in gill nets, shad comprised 61. 5 percent.
The data given in Table 2 is a consolidation of data which served as the basis for
locating or relocating the wire traps.
In Table 3 consolidated gill net collection data are broken down to show ares of
netting and the ratio of crappie to all other species caught. The number and percentages
of crappie tagged are given by area in Table 4. In all, a total of 1,493 crappie were
tagged during the eight months covered by this report.
In the Nolan River Area, 144 crappie were caught in the wire traps. These repree
sent 9.64 percent of the total tagged during the year. Of these, five were recaptured
in the same area and represent 0.03 percent of the total crappie tagged or 10.62 percent
of the 47 tags recovered during the study period.
In the Upper Lake Area, 238 crappie, or 15.94 percent of the total, were tagged
during this segment. Seventeen tagged fish were recovered, which accounted for 9.96
percent of the total tagged fish released, or 34.05 percent of the total tagged fish
recovered during the year. One fish that had been tagged the previous year was also
recovered.
There were 1,109 crappie tagged in the Middle Lake Area, which amounted te 74.28
percent of the yearly total of marked fish. In this same area 25, or 0.02 percent of
the total fish tagged this year, were recovered along with four crappie that had been
tagged and released in earlier study periods. The 29 returns comprised 53.19 percent
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who
of the total tagged fish recovered during the year.
Four traps were used in the Lower Lake Area, but only during the months of
November, 1959 through January, 1960. Two crappie were caught and tagged during that
period. A fisherman later recovered one of these and it comprised 2.13 percent of the
total tagged fish recovered during the year. ,
Information concerning all tagged crappie recaptured by either fishermen, gill
nets, or traps is listed in Table 5. Two crappie traveled 30 miles, one traveled three
miles and four traveled two miles each. The remaining tagged crappie either traveled
shorter distances or had no travel at all. With the exception of the few fish mene=
tioned, the movement of crappie based on tagged fish recaptured during periods other
than the spawning season is indistinct. No pattern or trend of movement is indicated.
As a matter of fact 33 tagged crappie, recaptured during the year, traveled less than
100 yards, and are shown in the distance traveled column of Table 5 as "none".
It seems apparent that tagged crappie do not tend to move very far from the place
where they were released. For example, Tag Number 287 was placed on a crappie on June
12, 1957. This fish was recaptured on April 6, 1960, after a period of almost three
years, within one mile of the place where it was originally tagged and released. A
fish, with Tag Number 2,264, was recaptured after being free for 405 days within two
miles of the place of tagging. Another, with Tag Number 1,028, remained free for 280
days and was recaptured at the original point of tagging and release. Still another
fish, carrying Tag Number 2,974 and free for 258 days, was recaught within two miles
from where it was released. The only other fish to remain free more than 100 days was
recaptured within 100 yards of the point of release.
Weekly lake level elevation readings are presented in Table 6. The lake maintaine
an almost constant level throughout the year, varying only 3.2 feet from its lowest
level to its highest. Week to week changes in lake level were slight, and so far as is
known had little or no effect upon the crappie in Lake Whitney.
As a matter of record, Table 7 includes temperatures taken at the mouth of Cedar
Creek on Lake Whitney for the months of June, July, and August. Comparable temperatures
are given for June 1957; July 1957 and 1959; and August 1957.
As shown in Table 8, only one crappie was taken in seine samples and this was a
crappie fry. Gizzard shad were predominant in the catch, comprising 84.28 percent of
the fish seined. The sharpnose shiner, Notropis oxyrhynchus, was next in abundance
with 4.90 percent of the seined specimens, and Gambusia affinis followed with 3.10
percent. Bluegills, easily caught in the wire traps, comprised only 2.58 percent of the
388 specimens seined.
The study thus far has been primarily concerned with the tagging and recapture of
adult crappie and this work has indicated that, barring exceptions, tagged crappie tend
to remain relatively near the original point of capture and release. With this in mind,
it seems apparent that the emphasis of the study should be shifted to the study of
crappie fry and spawning success. This will be the major part of the work during the
i ' t a e
coming year's study “be
Prepared by Dwane Q. Smith Approved by f é aptore
Assistant Project Leader Director Inland Fisheries Division
Date February 14, 1961
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Table 1. Fish caught in wire traps in Lake Whitney, November 1959 through June, 1960.
Species
Lepisosteus oculatus
L. osseus
Spotted gar
Longnose gar
Gizzard shad Dorosoma cepedianum
Ictiobus bubalus
Smallmouth buffalo
River carpsucker
Carpiodes carpio.
Carp Cyprinus carpio
Ictalurus punctatus
Channel catfish
White bass
Roccus chrysops
Pylodictus olivaris
Micropterus salmoides
Flathead catfish
Largemouth bass
Warmouth Chaenobryttus gulosus
Bluegill Lepomis macrochirus
White crappie Pomoxis annularis
Aplodinotus grunniens
a
Freshwater drum
Totals
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abe
Table 2. Results of gill net collections, Lake Whitney, November 1, 1959 through October 31, 1960.
Percent of | Weight Percent of Average weight] Fish per 100 [Weight (lbs.
Species ex Total number in pounds Total weight in pounds feet of net per 100 feet
: of net
Spotted gar 2h. 74 0.41
Longnose gar 261.62 4,29
Gizzard shad 342.53 5.62
Smallmouth buffalo 23.84 0.39
River carpsucker 45.76 . 0.75
Carp | 15.74 0.26
Channel catfish 122.68 . 2.01
White bass 4h 20 0.72
Spotted bass os 0.77 0.01
Largemouth bass 38.56 0.63
Warmouth bass 0.30 0.05
Bluegill sunfish 2.85 0.05
White crappie 37.17 0.61
Freshwater drum 8.86 0.15
Totals 1862 | 100.00 969.62 100.00
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Table 3. Crappie and other species caught in gill nets in Lake Whitney, November 1959 through October 1960.
| Average weight | Fish caught
in grams other than
o cra pris.
Percent of
total crappie
J caught
Average length
Feet of
in millimeters
netting
_j|._used.
Period
Brazos River July 1960 113
Upper Lake November 1959 120
Area thru
October 1960
Middle Lake November 1959 TT
Area thru
October 1960
100.00 1,360
Totals
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oB=
Table 4. Summary of crappie tagging and recapture data, Lake Whitney, November 1959 through. October 1960.
Nolan River
Upper Lake
Area
Middle Lake
Area
Lower Lake
Area
Totals
Trapping and Tagging
Number [ Number | Number
Period [traps used taken on
Percent of |
total tagged
erappie
recaptured
March
thru
June
November
thru
October
November
thru
October
November
thru
January
*Includes five crappie tagged during previous segments.
Percent of
total tagged
fish recap-
tured in area
10.63
34.05
53-19
Geld
100.00
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Table 5.
Tag No.
287
1024
1028
1073
1108
1112
1116
1132
a
1150
1160
1165
1173
1199
1202
1221
1235
1237
1259
1276
1277
1283
1291
1292
1292
1303
1315
1329
1339
1341
1355
1390
1he9
~ Ta
fe
Date
6-12-57
8-27-59
9= 3-59
1-18-60
1-27-60
1-27-60
2= 3-60
2=- 8-60
2-18-60
2-18-60
3- 3-60
3= 4-60
3= 4-60
3-17-60
3-17-60
3-21-60
3-22-60
3-22-60
3+25-60
3-28-60
3-28-60
3-28-60
3-28-60
3-28-60
3-28-60
3-28-60
3-29-60
3-29-60
3-29-60
he 5-60
= 5=60
he 5-60
he 7=60
Information
___Location _
Juniper Cove
Near Herringtons
Near Herringtons
Deep Canyon
Mesquite Creek
Lakeside Village
Juniper Cove
Juniper Cove
Mesquite Creek
Mesquite Creek
Deep Canyon
Nolan River
Nolan River
Nolan River
Mesquite Creek
Mesquite Creek
Juniper Cove
Juniper Cove
Deep Canyon
Mesquite Creek
Mesquite Creek
Near Herringtons
Juniper Cove
Juniper Cove
Juniper Cove
Cedar Creek
Wann Canyon
Mesquite Creek
Juniper Cove
Nolan River
Nolan River
Juniper Cove
Wann Canyon
he 7-60
4-23-60
Air Force Base
Hillcrest Dock
Near Herringtons
Hillcrest Dock
Mesquite Creek
Greer's Barge
Juniper Cove
Juniper Cove
Mesquite Creek
Mesquite Creek
Air Force Base
Nolan River
Nolan River
Nolan River
Mesquite Creek
Mesquite Creek
Juniper Cove
Wann Canyon
Deep Canyon
Greer's Barge
Mesquite. Creek
Near Herringtons
Air Force Base
Juniper Cove
Juniper Cove
Air Force Base
Wann Canyon
Mesquite Creek
Wann Canyon
Nolan River
Nolan River
Juniper Cove
Wann Canyon
Tagged crappie recaptures in Lake Whitney, November 1, 1959 through October
1030
80
Distance Traveled _
1 mile upstream
2 miles downstream
none
£ mile
none
WF
W
+ mile
none
2 miles
none
iii
4 mile
none
Lia
2
5 mile
none
i
1 .
5s mile
none
wt
"W
w
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=1O0@8
Table 5. Tagged crappie recaptures in Lake Whitney, November 1, 1959 through October 31, 1960.
(continued )
Taggi Information Recapture Information
Tag No. Date Location Date Location Days of Freedom Distance Traveled
1436 he 7-60 Wann Canyon 4=16=60 Air Force Base 9 $ mile
140 he 7-60 Wann Canyon 4-22-60 Wann Canyon a6 none
1463 he 8-60 Mesquite Creek 4-21-60 Mesquite Creek 13 on
1472 4-11-60 Nolan River July Little Rocky 9O** 30 miles downstream
1487 4-12-60 Mesquite Creek 7-23-60 Mesquite Creek 102... none
1h9h 4-12-60 Lakeside Village 5-22-60 Near Brazos Point ho 30 miles upstream
L495 4-12-60 Lakeside Village 5-17-60 Lakeside Village 35 none
1514 4-13-60 Near Herringtons 4-31-60 Cedar Creek area 19 a
1563 4-18-60 Mesquite Creek 5-11-60 Mesquite Creek 23 a
1619 4-21-60 Juniper Cove 4-22-60 Cedar Creek Dock 1 + mile
1651 5=- 3-60 Mesquite Creek 5-14-60 Near Circle "D" 11 3 miles
1665 5- 4-60 Lakeside Village 5-17-60 Lakeside Village 13 none
1726 5-19-60 Juniper Cove 6= 4-60 Cedar Creek 16 ¢ mile
226) 2-24-59 Lakeside Village he 3-60 Mesquite Creek 4.05 2 miles
2974 7-21-59 Near Herringtons he he60 Juniper Cove 258 2 miles
720 9-19-60 Bluff #8 Marker 9=27-60 Bluff #8 Marker 8 none
920 9-14-60 Bluff #8 Marker 10-13-60 Bluff #8 Marker 29 i
928 9-14-60 Bluff #8 Marker 10-13-60 Bluff #8 Marker 29 «
936 9-14-60 Bluff #8 Marker 10-13-60 Bluff #8 Marker 29 "
* ‘These fish were recaptured more than once.
** Approximate
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-ll-
Table 6. Lake Whitney water level elevations, November, 1959 through October, 1960.*
Date Lake Elevation (m.s.1.)
November 4, 1959 519.94
November 11, 1959 519.88
November 18, 1959 519.65
November 25, 1959 519.98
December 2, 1959 520.00
December 9, 1959 519.66
December 16, 1959 520.16
December 23, 1959 519.89
December 30, 1959 519.86
‘January 6, 1960 521.415
January 13, 1960 520. 34
January 20, 1960 520.00
January 27, 1960 519.76
February 3, 1960 520.00
February 10, 1960 519.05
February 17, 1960 519.36
February 24, 1960 , 520.16
March 2, 1960 519.90
March 9, 1960 519.97
March 16, 1960 519.82
March 23, 1960 519.92
March 30, 1960 519.69
April 6, 1960 519.48
-April 13, 1960 519.03
April 20, 1960 518.76
April 27, 1960 519.63
May 4, 1960 519.76
May 11, 1960 519.97
May 18, 1960 519.75
May 25, 1960 519.85
June 1, 1960 520.02
June 8, 1960 519.76
June 15, 1960 519.70
June 22, 1960 519.20
June 29, 1960 519.10
July 6, 1960 518.80
July 13, 1960 518.67
July 20, 1960 520.17
July 27, 1960 519.94
August 3, 1960 520.00
August 10, 1960 519.96
August 17, 1960 519.82
August 24, 1960 519.75
August 31, 1960 519.60
September 7, 1960 519.28
September 14, 1960 518.92
September 21, 1960 518.50
September 28, 1960 518.71
October 5, 1960 518.36
October 12, 1960 517.98
October 19, 1960 518.03
October 26, 1960 520.22
*Normal surface elevation is 520 m.s.l.
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1D»
Table 7. Lake Whitney water temperatures .*
*Temperatures recorded at regular
station located at mouth of Cedar Creek
ugust 13,
1960 __
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«13~
Table 8. Results of seine collections, Lake Whitney, November 1959 through
October, 1960.
Scientific name
Species Percent of Total
Spotted gar Lepisosteus oculatus 0.26
Gizzard shad Dorosoma cepedianum 84.28
River carpsucker Carpiodes carpio | 0.26
Sharpnose shiner Notropis oxyrhynchus 4.90
Brazos shiner Notropis brazosensis 1.54
Blacktail shiner Notropis venustus 0.51
Red shiner Notropis lutrensis 0.51
Gambusia Gambusia affinis 2.10
Largemouth bass Micropterus estes 1.80
Bluegills Lepomis macrochirus 2.58
White crappie Pomoxis annularis 0.26
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Figure 1. Side of an ex-
perimental trap which was
designed to extend through
the thermocline, showing
throat extending vertically
from top to bottom.
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Figure 3.
Two type
capture crappic.
of traps used to
Figure 4. Trap with a funnel
throat at either end.
type
-cT-
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RIVER
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om
Kimball Bend
Kimball Rec. Area
Indian Lodge
Plowman Creek 7c
Raymond Creek
Mesquite Creek
Lakeside Village
Circle "D" Dock
Steel Creek
Cedron Creek
King Creek
Nob Hill
Rocky Creek Lodge
Little Rocky Lodge
Sportsman's Park
Towash Creek
Whitney Creek
State Park
Katy Railroad Bridge
Elm Canyon Lodge
Hillcrest Camp
Redwood Lodge \
MIDDLE
8
os
Deep Canyon 7a ea
Wann Resort LAKE
Cherokee Lodge
Waldock's Lodge AREA
T&L Boat Dock
Gav's Juniner Cawa
Add gum y NOLAN RIVER