TPWD 1955 F-2-R-2 #165: Inventory of Species Present in the Belton Reservoir, Texas
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STATE ___rexas
_ PROJECT F-2-R-2, Joo B-l
It f PERIOD June 1, 1955 through May 31,1955
Job Completion Report
by
Kenneth C. Jurgens
TITLE
Inventory of Species Present in the Belton Reservoir, Texas.
OBJECTIVES
To determine the species present and their relative abundance, as well as to
determine the ecological factors influencing their distribution.
METHODS
Since the Belton Reservoir is a newly impounded body of water, and since it
had not filied to the expected normal pool elevation during the study period, and since
the lake level varied considerably from month to month, no regular netting or seining
stations could be established.
All net and seine collections were therefore made at random, with the purpose
of making as many collections as possible from the varied habitats during the alloted
e.
Specimens were collected through the use of small meshed seines, experimental
and regular gill nets, and fyke nets. Seined specimens were preserved in a solution
of formalin (10 per cent) for later identification in the laboratory. Netted specimens
were identified, weighed and measured at the lake. Data was recorded for netted indivi-
duals of the game spécies and in some cases for individuals of the forage and rough
species. This data included: length, weight, sex and stage of sexual development. If
any game fish specimens were found to have food in their stomachs, these stomachs were
preserved for laboratory examination.
Water samples were collected regularly from a station established soon after
the gates on the dam were closed and water began to be impounded.
A one day creel census was made on Armistice Day, November 11, 1954, in order
to sample the type of fishing pressure presently being exerted on the fish population
in the reservoir.
DESCRIPTION OF THE BELTON RESERVOIR
The following description of the Belton Reservoir Area was taken in part from
material provided by the U. S. Army Corps of Engineers, in that portion of the Master
Plan for the Belton Reservoir entitled Biological Potentialities.
"4-03. Soils and vegetation.- The soils in the pro-
ject area represent various stages of development.
The alluvial soils of the bottom lands are sandy
loams and clay loams. The residual soils are clays,
stony clays, and rocky soils...
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“ ‘ + 2.
4-O4. Only remnants of the bottom timbers remain
since a large percentage of the bottom lands have
been cleared or selectively cleared for cultivation
and pecan production. Tree growth and ground cover
of the lowlands consists principally of pecan,
American elm, cottonwood, willow, walnut, box elder,
sycamore, bur oak, hackberry, water ash, buckeye,
Johnson grass, bermuda grass and ragweeds. Vegeta-
tive cover on the slopes and uplan’s consists princi-~
pally of blackjack oak, post oak, live oak, cedar,
hackberry, persimmon, skunkbrush, buffalo grass,
grama grass and bluestem. These rough slopes and
uplands have been subject to overgrazing and burning
and the better areas provide only fair pasture.
eames CHEESY RARER ENE NONRTORRAR Same
The reservoir lies in the Lampasas Cut Plains, a
physiographic subdivision of the Great Plains Pro-
vince. To the east of the Belton project is a roll-
ing prairie and to the west is a heavily timbered
region. The major streams have cut sharply into the
terrain leaving U-shaped valleys varying in width
from about one-quarter to more than one mile, and
varying in depth from about 70 to 200 feet.
4-05. Physical features of the reservoir area.-
406. Physical features of the reservoir basin. -
The reservoir lies in the narrow and tortuous valley
of the Leon River and the relatively straight valley
of Cowhouse Creek, the principal tributary of the
Leon River. At the top of conservation pool, ele-
vation 569, the lake will extend about 22 miles up
the Leon River Valley and about 8 miles up the Cow-
house Creek Valley. The irregular shoreline will
be about 110 miles in length. Most of the shore
is steep, and only a small amount can be considered
Plat."
At the end of the study period the reservoir had filled to elevation 554 and
covered 5,170 surface acres with 118,000 acre feet of water. At conservation pool
elevation the lake will cover 7,400 acres with a maximum depth of 99 feet. Of this
area 21% will be less than 10 feet in depth, indicating large areas of shoal which
should provide adequate spawning grounds for the game species.
"Access to the west side of the lake between Cowhouse and Owl Creek will not
be available to the general public..., except by water craft. The Cowhouse Creek arm
of the reservoir which includes about one-fourth of the water surface of the lake will
be needed for military use in the proposed military expansion program.”
FINDINGS
Table I contains a checklist of the species found to occur in the Belton
Reservoir. In all, a total of 56 seine and 75 net collections were made during the
two years the lake was under study. These collections provided a total of 9,607
ined specimens and 1,084 netted specimens or a grand total of 10,688 specimens,
representing 38 species and 10 fish families. The results of these collections are
presented in Tables II and III.
In Chart A. are presented the results of analyses made on the stomachs of 36
white crappie and 51 channel catfish.
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’ 3.
Of the large mouth bass collected, only the stomachs of six were found to contain
food remains. This food had a total volume of 69 ml., of which 44 ml. was composed of
the remains of white crappie, 21 ml. was composed of gizzard shad remains and 4 ml. com-
posed of the remains of small sunfish.
The stomachs of four spotted bass contained food remains totaling 14.5 ml.
This was composed of gizzard shad, 8.0 ml.; white crappie, 6.0 ml.; and unidentified
fish remains 0.5 ml.
; Three drum stomachs contained 20.62 ml. of food remains. Earthworms make up
the bulk of the total with 14.0 ml. Sunfish remains were next with 6.5 ml. while the
remains of dipterous or fly larvae and vegetation comprised the other 0.12 ml.
Two flathead catfish stomachs contained a total volume of 33.0 ml. of food re-
mains. Most of this, 24.0 ml., was composed of fish to badly digested to identify.
Cockleburrs and algae made up the other 9.0 ml.
A single yellow bullhead stomach containing food was found. This food totaled
only 1.02 ml. and was made up entirely of insect remains including damselflies, beetles
and chironomids.
Only two warmouth bass stomachs containing food remains were examined. These
specimens contained a volume of 12 ml. of partially digested food. The bulk of this
food was composed of earthworms (9.0 ml.) and the remainder was composed of crayfish
(3.0 ml.).
Data recorded at the temperature and water sampling station are presented in
Tables IV and V. This station was established in the open lake near the dam in July,
1954 and the data shown are for the period from July 1954 through May, 1955.
Sechi disc readings were taken during the same period as temperatures and
water samples. These varied from 19.5 inches to 72.0 inches, with an average of 39.25
inches for the year. The readings were obtained from the lower end of the lake where
the water is normally the clearest. The upper end of the lake, which is rapidly af-
fected by rises on the Leon River, often turns red with silt when runoff is heavy.
Chart B. presents a monthly reading of reservoir elevation, the approximate
surface acreage and the acre footage for the months June, 1954, through May, 1955. At
its highest level, in May 1955, the Belton Reservoir covered 5,170 acres and contained
118,000 acre feet. of water. Its greatest depth during the period was 63 feet.
Tables VI through X present data concerning weights and "K" factors for indivi-
duals of given total lengths for 19 of the species collected in the reservoir. Total
lengths are given in inches and weights are given in pounds and tenths of pounds for
most of the specimens. The weights of some smaller individuals are given in grams where
they weigh less than 0.1 pounds. "K" factors were based on standard length in mm. and
weight in grams.
In Table XI are given the results of a one day creel census taken in an effort
to sample the type of fishing pressure being exerted on the fish population. The table
shows the number of fish caught, the number of hours spent fishing and the return per
unit of effort in numbers of fish per man hour, for the various species taken, the
methods of fishing employed and the types of baits used. It needs to be pointed out
that the figures shown are based only on pure catches of each species shown, or as in
the case of sunfish, for all types of sunfish, and for fish caught when only a single
method or type of bait was used.
%
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DISCUSSION AND CONCLUSIONS
Work during the study period conclusively proved the existence of a large
crappie population in the reservoir. These fish were frequently seined and netted and
ranged in total length from 2 to 14 inches, and from 1.5 grams to 1.6 pounds in weight.
Of the netted crappie, the average total length was 12 inches and the average weight
was 0.9 pounds.
Crappie accounted for 15.2 per cent of the specimens netted during the period
June, 1954 through May, 1955 and for 14.2 per cent of the specimens netted over the two
year study period. Regardless of their apparent abundance, however, this species has
not yet been taken in appreciable numbers by sport fishermen. This may be due in part
to the abundance of forage fish in the reservoir. For example: Gizzard shad taken in
nets accounted for 12.7 per cent of the total netted catch over the two year period.
(Table I) Redfin shiners and blacktail shiners together comprised 55.4 per cent of the
seined specimens and the other ten forage species increased this per centage to more
than 67 per cent. (TableII)
Of the 36 crappie stomachs found to contain food, 91 per cent of the food was
composed of shad. (Chart A.)
It seems plausible that a species, such as the crappie, which prefers dense
cover and is provided with both excellent cover, in the form of brush and trees left
standing in the reservoir basin, and with an abundance of food fishes to prey upon,
would be difficult to take on the rod and reel with either live or artificial bait.
So far this has been the case in the Belton Reservoir.
Carp and carpsuckers are also very abundant in the Belton Reservoir. The two
species accounted for more than 30 per cent of the specimens netted during the two
years of the study. The average size for carp was 9 inches in total length and for
carpsuckers was 15 inches. Fortunately, many fishermen of the Temple-Belton area do
not object to these species and large numbers of fishermen specifically go the lake
to fish for carp and sucker type fish. The method commonly employed when fishing for
carp or suckers has been bank fishing with pole and line, baited either with doughbait
or worms. There is no doubt, however, that these two species along with the gizzard
shad will have to be controlled in the near future.
Since the lake now covers large areas of what were formerly cultivated fields
of sandy loam, it might be possible, in the future, to bait areas which could be dragged
with large haul seines. If this were done during the spawning season, it is concievable
that the populations of carp and carpsuckers could be effectively cropped.
; Gizzard shad comprised better than 12 per cent of the netted specimens and
nearly 5 per cent of the seined specimens over the two years. For the present, at least,
this species is not a major problem although their future control will be necessary. This
could be effected through the use of rotenone as a selective poison.
Like the gizzard shad, the combined species of sunfish comprised approximately
12 per cent of the netted specimens and more than 13 per cent of the seined specimens.
The bulk of these specimens were under seven inches in total length and are of a size
not desirable to most fishermen. Some form of control of these species which will help
to crop the population also needs to be devised or it is certain that these fish will
soon be overly abundant.
Like the crappie, channel catfish are more abundant in the lake than is apparent
in the catch of the sport fisherman. The species accounted for nearly 10 per cent of the
total netted specimens during the study period.
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5.
The channel catfish taken ranged in size from 9 to 25 inches and in weight from
0.45 pounds to 6.9 pounds. The average netted catfish was found to be 15.5 inches long
and weighed 1.6 pounds. This species has not been frequently taken by fishermen.
Perhaps the most apparent reason for this is the fact that the lake bed, as it
was covered by the rising water level, contained many earthworms which, when covered by
water, tried to escape by coming out of the ground and were eaten in quantities by
channel catfish. Earthworms were found to be more than 36 per cent of the diet in the
contents of 51 channel catfish stomachs examined. (Chart A.)
Likewise, yellow, or flathead catfish, are relatively abundant, making up ap-
proximately one per cent of the total catch. The presence of this species is a definite
asset to the lake both as an effective predator and as a desirable sport species.
Large mouth bass, though not taken in large numbers in either seine or net col-
lections are apparently fairly numerous in the Belton Reservoir. Judging from the number
taken during one day's fishing by 74 fishermen, the relative abundance of this species
seems to be fairly high. (Table XI.)
The fact that the Belton Reservoir was not full during the study period made
work in the area relatively difficult. Much of the shoreline and much of the shoal
area of the lake was covered with peach, plum and pecan orchards as well as scrub cedar
and scrub oak. It was not until the last month of the study period that sufficient
water was impounded to place the shoreline at a level where the trees and brush had
been removed. If this level is maintained, or if the lake level rises, it should be
somewhat easier for fishermen to fish the lake and the fish may be forced to leave the
heavier cover, with which the floor of the reservoir basin is covered.
The one day creel census, taken on Armistice Day, 1954 revealed the following
information: Seventy four fishermen, in 176.5 hours caught 62 fish. This was at the
rate of one fish every 2.9 hours or 0.35 fish per man hour. Sunfish were caught at the
rate of 1.3 fish per man hour, largemouth bass were caught at the rate of 1.0 fish every
2.5 hours and carp were caught at the rate of 1.1 fish per hour.
Of the total hours spent fishing by the 74 fishermen, 140.5 hours out of 176.5
hours, or 79 per cent of the time, was spent in still fishing from the bank. During
only 21 per cent of the hours fished, were the people engaged in trolling from boats.
The average fishing trip lasted 2.4 hours and produced 0.8 fish per fisherman.
The fact that most of the fishing in Belton Reservoir was done from the shore
indicates either one of two things. Either the fishermen using the lake prefer shore
fishing to boat fishing or there are not enough boats to go around. The latter is
more probably true. This strongly indicates a need for additional boat liveries to
supplement the service now being given by the existing two dock operators.
RECOMMENDATIONS
1. It is recommended that further study of the Belton Reservoir be made to
determine a method or methods of controlling the gizzard shad, river carpsucker, carp
and sunfish populations.
2. It is also recommended that this lake be opened to contract fishermen,
3. It is further recommended that both state and federal fish hatcheries be
instructed not to stock any of the species of sunfish or crappie since both types
of fish are already present in relative abundance.
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ON
SUMMARY
1. Belton Reservoir lies in the rough, tortuous valley of the Leon River and
the relatively straight valley of Cowhouse Creek, Texas.
2. The Reservoir now covers approximately 5,000 surface acres, or roughly 71%
of the surface acreage expected at conservation pool elevation.
3. About one fourth of the surface acreage of the lake will be used for mili-
tary purposes and shall not be available to the general public.
4. 10,688 specimens, representing 8 species of fish were collected during the
study.
5. Catfish and crappie are present in greater abundance than the results of
sport fishing would indicate.
6. Largemouth bass also are relatively abundant.
7. Gizzard shad, river carpsuckers and carp are multiplying rapidly and will
need to be controlled in the near future.
8. Of the crappie collected, 91% of their food, based upon the contents of
36 stomachs, was composed of gizzard shad.
9. Of the channel catfish, earthworms comprised the most frequent food, being
36 per cent of the total volume of food remains in 51 stomachs.
10. Based on one day's creel census data, 79 per cent of the time spent fish-
ing on Belton Reservoir is devoted to bank fishing, the average fishing trip lasted
2.4 hours and fish were caught at the rate of 0.8 fish per fisherman per trip.
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0.08% insects
crappie
White unidentified
Crappie ' fish
36 }
Stomachs
gizzard
shad
earthworms
36.4%
nidentified
fish, minnows
Uu
6.64%
: and suckers
‘Channel - ti
Catfish
51
. Eg Stomachs i
sunfish and
crappie
vegetation gizzard shad
and
detritus
29.7%
Chart "A" ~ Results of Stomach Analyses, Belton Reservoir,
June 1953 through May 1955.
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ELEVATION | SURFACE AREA STORAGE AREA
IN FEET JUNE JULY AUG SEPT OCT NOV DEC JAN FEB MAR APR YI IN ACRES IN ACRE FEET
Chart "B" - Reservoir Elevation, Surface Area Inundated and Storage in Acre Feet, Belton Reservoir,
June 1954 - May 1955.
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Checklist of Species, Belton Reservoir.
Scientific name
1. Lepisosteus platostomus
2. Lepisosteus productus
3. Dorosoma cepedianum
4. Cycleptus elongatus
5. Ictiobus bubalus
6. Carpiodes carpio
7. Moxostoma congestum
8. Cyprinus carpio
9. Notemigonus crysoleucas
10. Notropis atherinoides
ll. Notropis venustus
12. Notropis lutrensis
13. Notropis volucellus
14, Notropis buchanani
15. Pimephales vigilax
16. Pimephales promelas
17. Campostoma anomalum
18. Ictalurus punctatus
19. Ameirus melas
20. Ameirus natalis
21. Pilodictus olivaris
22. Schilbeodes mollis
23. Fundulus natalis
24. Gambusia affinis
25. Micropterus punctulatus
26. Micropterus treculi
27. Micropterus salmoides
28. Chaenobryttus coronarius
29. Lepomis cyanellus
30. Lepomis microlophus
31. Lepomis macrochirus
32. Lepomis humilis
33. Lepomis megalotis
34. Pomoxis annularis
35. Hadropterus scierus
36. Percina caprodes
37. Etheostoma spectabile
38. Aplodinotus grunniens
Common name
shortnose gar
spotted gar
gizzard shad
blue sucker
smallmouth buffalo
river carpsucker
grey redhorse
carp
golden shiner
emerald shiner
spottail shiner
redhorse or red shiner
mimic shiner
ghost shiner
parrot minnow
fathead minnow
stoneroller ;
southern channel catfish
black bullhead
yellow bullhead
yellow catfish
tadpole madtom
blackstripe topminnow
common mosquitofish
Kentucky spotted bass
Texas spotted bass
largemouth bass
warmouth
green sunfish
redear sunfish
bluegill sunfish
orangespotted sunfish
longear sunfish
white crappie
dusky darter
Logperch
orangethroat darter
freshwater drum
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Table II
Results of Netting Collections, Belton Reservoir, June 1953 through May 1955.
1954 1955 % OF 1953- 1953- % OF
SPECTES JUNE JULY AUG SEPT OCT NOV DEC JAN FEB MAR APR MAY TOTAL TOTAL 1954 1955 TOTAL
TOTAL TOTAL 53-55
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melas
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salmoides
coronarius
cyanellus
macrochirus
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Table TII
Results of Seining Collections, Belton Reservoir, June 1953 through May 1955.
1954 1955 1954- 1953- GRAND 4% OF
SPECIES JUNE JULY AUG SEPI OCT NOV DEC JAN FEB MAR APR MAY 1955 1955 TOTAL TOTAL
TOTAL TOTAL
L. platostomus O 0 0 0 @) ) re) 0 0 0 0 1 1 16 17 0.18
D. cepedianum 21 23 6 ) 8 0) Oo 15 Oo 12 127 8 220 240 4.60 4.79
Carpiodes carpio 0 ) O 0 ) ) 0 0 ) 0 0 0 O 18 18 0.19
M. congestum 0 0 0 ) 0 0 0 2 0 0 0 1 3 7 10 0.10
Cyprinus carpio 3 0 © fe) 1 9) ) 3 @) 3 8 ) 18 14 32 0.33
N. crysoleucas LO 7 6) O wi 0) 10) O 0 ) O° 0 2h. 2 26 0.27
N. atherinoides O ) O O 6) O ©) O 0 ) ) 3 3 O 3 0.03
N. venustus 1 O 107 Oo 456 ) Oo eal 0 170 193 280 1228 366 1594 16.59
N. lutrensis 51 99 183 O 754 0 Oo 102 O 169 154 178 1690 20hk5 3735 38.88
N. volucellus re) ) 0 0 0 ) O 0 0 0 0 0 0 7h Th 0.77
N. buchanani 0 0 @) 0 ) @) fe) 0 O O 0 re) 0 71 71 0.74
P. vigilax 1 2 0 0 7 @) 0 i 0 0 O 1 12 341 353 3.67
P. promelas ) 0 O @) ) 0 re) @) 0 O 0 0 0 50 50 0.52
C. anomalum ) ) ) ) ) ) 6) fe) ) fe) 0 O ) 94 9h. 0.98
I. punctatus 0 O 0 O 0 fe) ) O 0 0 0 0) 0 150 150 1.56
A. melas 6) 0) 0) 6) 0) 0 0) 2 0 0) 0) 0) 2 ) 2 0.02
A. natalis @) 0 0 ) ) 0 0 ) 0 O 0 0 0 4 y 0.04
P. olivaris O ©) 0 0 0 0) @) 0 0 0 1 0 1 7 8 0.08
S. mollis fe) ) O 0 0 fe) ) re) 0 0 0 0 0 orn 9k 0.98
F. notatus O 0 0 0 0 0 ) 0 0 0 0 0 0 22 22 0.23
G. affinis 18 7 16 oO 168 ) ) 7 0 206 71 12 573 195 768 7.99
M. punctulatus 25 10 5 ) 6 0) ) ) O O @) fe) 46 64 110 1.14
M. treculi 0 @) re) Oo 15 O 0) 2 ) 1 5 1 2k 1 25 0.26
M. salmoides 12 ye k ) 1 ) ) 7 Oo ill 8 2 kg 9 58 0.60
C. coronarius 0 0 0 0 0 0 fe) 0 0 0 1 0 1 0 1 0.01
L. cyanellus 22 fe) 6 re) 1 fe) fe) 5 0 1 7 fe) he 53 95 0.99
L. microlophus O ie) ie) O ie) O O 0 e) 0 O 2 2 0 2 0.02
L. macrochirus 97 24k 698 Oo 196 fe) Oo 34 O 31 175 8 663 We 680 7.08
L. humilis 6 O 0 0 ©) ) ¢) ) 0 0 0 ) 6 31 37 0.39
L. megalotis 25 52 «23 0 @) 0 ) 1 Oo. 28 2 7 138 375 513 5.34
P. annularis 62 56 2 ) 3) ) ) @) ) Oo 57 1 178 106 28h 2.96
H. scierus ) 0 0 @) @) 0 fe) 9) @) @) 0 O 0 10 10 0.10
P. caprodes 0 0 ©) ) 0 fe) fe) @) ) 0 @ 1 i 14 15 0.16
E. spectabile 1 iF 1 ) fe) ) ) ) 0 0 0 © 6 186 192 2.80
ToT 7s 355 356 451 O 1620 O ) ? O 632 809 506 4931 4676 9607 ¢ 9
--- Page 12 ---
Table IV
Temperatures-°F, Belton Reservoir, July 1954 through May 1955.
DEPTH IN
FEET JULY AUG. SEPT. OCT. NOV. DEC. JAN. FEB. MAR.
O 88 87 79-5 73 63 60 53 a3 60
1 87 87 79 73 62 60 53 53 60
ra 87 87 19 73 62 60 53 53 60
3 87 87 19 73 62 59 53 53 60
4 87 87 79 73 62 59 52.5 53 60
é, 87 87 19 73 62 59 52.5 on 61
6 87 86 79 73 62 59 52.5 52 61
7 87 85 19 72:5 62 59 52 52 61
8 86 85 79 72.5 62 58.5 52 52 61
fe) 86 85 79 72.5 62 58.5 52 52 61
10 86 85 79 72 62 58.5 52 52 60.5
11 85 6h. 78 72 62 58.5 52 52 60.5
12 85 8h 78 72 61 58.5 52 52 60.5
13 8h 84 78 72 61 58.5 52 52 60.5
LA 83 8h 78 72 61 58.5 52 52 60.5
15 82 8h 78 72 58.5 58.5 52 52 60
16 80 8h 77.5 72 61 58.5 52 52 59
by 80 83 77 72 60.5 58.5 52 52 vis
18 80 83 77 72 60 58.5 5e 52 56
19 79 83 76 72 60 50.5 52 52 55
20 79 82 76 71.5 60 58.5 52 52 55
21 719 81 76 71.5 60 58.5 52 52 55
22 79 80 76 71 60 58.5 52 52 55
a3 re) 80 76 71 60 58.5 52 ae 55
ah 19 19 76 TA 60 58.5 52 52 pa)
a5 19 ae 75 rel 60 58.5 52 52 54.5
26 79 76 75 71 60 58.5 52 52 54.5
27 79 76 75 71 60 58.5 52 52 54.5
28 re) 76 75 Th 60 58.5 52 52 54.5
29 19 76 15 71 60 59 52 pe 54.5
30 19 76 75 71 61 59 52 52 54
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--- Page 13 ---
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°
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) ANVDARAD
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TIYdV HOUVN
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A STaeL
--- Page 14 ---
Table VI
Belton Reservoir, Total Lengths, Weights and "K" Factors, June 1954 through May 1955.
(Weights given in pounds unless otherwise indicated.)
INCHES NUMBER WEIGHT RANGE TOTAL WEIGHT WEIGHT AVG. "K" FACTOR RANGE TOTAL "Kk" AVERAGE "K"
Lepisosteus platostomus--shortnose gar
6.18
10.61
13.42
3.74
1.58
2.49
3.93
749
Wed
°
°
°
°
°
e
e
.
®
«
.
.
°
°
.
°
FUWWNEP PRR
HIO FU OnUM
ooo nononononone
WE FEE rwww
AWIWNO OWN
OCCOCCOOCOCO
W furor ou =
NPFUBDNMOWOOD
FWOOTWEE
oonenononononone
WEEFEE EE EU
NF w wo OMO OO
FWWNE PREP
FOO ONO MWO
4
7
8
2
L
1
i
2
1
Lepisosteus productus--spotted gar
e
°
.
.
.
FWWNHE PEPER
H ONO ONO OND
°
O.44 O.bh
0.67 0.83
0.62 0.99
1.24 1.2h
Lepomis cyanellus--green sunfish
hk pms 5 gms
3 gms 3 gms
19 gms 19 gms
35 gms 0.12
0.11 0.18
0.31 0.37
--- Page 15 ---
Table VIT
Belton Reservoir, Total Lengths, Weights and "K" Factors, June 1954 through May 1955.
(Weights given in pounds unless otherwise indicated. )
INCHES NUMBER WEIGHT RANGE TOTAL WEIGHT WEIGHT AVG. '"K" FACTOR RANGE TOTAL "K" AVERAGE "K"
Ictiobus bubalus--smallmouth buffalo
.
*
°
°
PREERHOOO
DAN OC MMW
OOUrD
cy
.
0.3
0.2
1.6
Kol
1.1
3.1
3-3
Ny ov -
°
°
Ictalurus punctatus--channel catfish
°
.
.
.
°
°
.
.
2
°
°
°
°
e
°
°
*
OWA AO ON AF FO OM FO
i
FPMM FW ONO O.\ONF OMOWN
NFOW FN Ph
NRFNOFEMFONNM OOUWD ©
NF ErOWAUD &
AAKH AA AO-~0
VENA FO OW FAA
°
.
°
°
°
°
e
WRWE ON NWW
°
.
.
ONUNUNOALEFORAN FW
e
°
°
°
NONNMUVUNWIWOW FOWWUT
NNMNNFRFPREPEPENNFENED
WONOCAO DOOMWONDOWOOWOH
°
°
WOrRAANA
MO
°
o
°
NAWNFWNEFPEFPRFEFOOCOOOO
ANFFNUNNNEFEFEOOOCO
ANFWNMNMNFEFFODODOOCCO
NMN EPR RP RP ENDER RE PE
NVMUNNYFPNYONNYANANNNND
VOM AOMNANIDOANUWO DY
OoONUANAWO
--- Page 16 ---
INCHES NUMBER WEIGHT RANGE TOTAL WEIGHT
OnA OW
wi Pf
Table VIII
Belton Reservoir, Total Lengths, Weights and "K" Factors, June 1954 through May 1955.
(Weights given in pounds unless otherwise indicated.)
Dorosoma cepedianum--gizzard shad
1 0.11 0.11
3 0.29 0.37
3 0.31 O.41
3 0.37 0.51
7 0.56 0.74
11 0.74 0.93
9 0.87 1.18
1 1.37 1.37
5 1.204 1.74
0.11
0.97
1.10
1.39
4.79
8.68
9.68
ee 3%
7.86
WEIGHT AVG. "K" FACTOR RANGE
° . .
ATA WDNOAN NAAN FE
FrRrFOCOOO°0O
WW ON NDFWW
Micropterus salmoides-- largemouth black bass
3 0.02 0.03
2 0.03 0.07
6 0.07 0.18
5 0.31 O.44
2 0.52 0.59
15 0.56 0.77
7 0.74% 1.00
1 1.18 1.18
i 4.99 «4.99
0.09
0.11
0.76
1.84
1.12
9.94
6.02
1.18
4.99
Chaenobryttus coronarius --warmouth
2 28 gms 35 gms
3 85 gms113 gms
1 142 gmsl42 gms
1 170 gms170 gms
63 gms
311 gms
142 ems
170 gms
Lepomis megalotis--longear sunfish
1 4 gms 4 gms
il 25 gms 57 gms
1 27 gms 57 gms
4 ems
1.05
a7 gms
0.03
0.05
0.12
0.36
0.56
0.66
0.86
1.18
4.99
313 gms
0.23
0.31
0.37
4. gms
433 gms
0.12
°
MNNrFPRrFNRFE WY
DWOO CO DAWOW
OR HFWFOOW ©
° °
e
WNHNNMNNMYEEE
MAOW AFA
FEOHUOMMOFON
.
MMMM NMNNN Pw
OW OW WW WW
.
cy e .
SIR ON UNF ©
2.19
2.49
3.87
2.92
2.73
2.79
2.64
2.74
3.54
TOTAL "K"
2.38
6.47
6.16
6.24
15 +39
24.05
20.46
2.31
11.51
6.10
4.19
15.92
13.40
D0 39
37.62
17.42
2.74
3.54
5.62
15.52
5.06
3.85
4 39
58.41
9-37
AVERAGE "K"
2.38
2.15
2.05
2.08
2.19
2.18
2.27
2.31
2.30
. . °
° ° °
WNhNwMNMNMN NM MW
WAN EV ANAC O
FE OOM OMow
.
--- Page 17 ---
Table IX
Belton Reservoir, Total Lengths, Weights and "K" Factors, June 1954 through May 1955.
INCHES NUMBER
MF OM OA OO
13
14
15
10
12
13
15
16
WEIGHT RANGE
(Weights given in pounds unless otherwise indicated.)
TOTAL WEIGHT
Carpiodes carpio--river carpsucker
3
i
15
10
3
h.
52
10
1
Cyprinus carpio-~-carp
m
2
9
38
Lh
4
7
ded
ww Po
FrRrFOOCOO00
°
ry
Re OOo oOo oO
a
.
°
°
WENO COON FWW
.
NONWMENRHEH
FON DAWONNMN
° .
WI
-
. ° °
o ° .
e
PRR r OOo O °°
ST ONID HEAT TNO PO
0.18
0.18
0.29
0.50
0.54
0.81
1.06
1.18
1.31
1.99
O.47
1.83
5.15
74
1.93
: 3.77
54.54
12.92
1.5
0.62
0.77
2.20
14.21
6.75
2.82
6.51
12.05
2.55
8.57
Ameiurus melas~-black bullhead
1
0
18
0.18
0.18
Aplodinotus grunniens--freshwater drum
F Pow Pf
0.81
1.68
4.68
3.12
0.86
WEIGHT AVG.
.
°
OFFER OUY
MPrRFrRFOOOOC°O
WN OO DFW FH
0.18
"K" FACTOR RANGE
ry ° .
° e °
OOO OF rR WE- ©
°
monMrynwmnmnmnwmnp
OoNw AAAAAI-~
2.92
ee
1.62
2.04.
2.47
2.71
2.63
2.58
24h
2.68
223 {
es
°
e
MONMNNNE
\Oo “A WS ©
hFNO OF ON
3.87
3.76
4.03
3.26
2.97
3.28
3.32
3.16
2.88
5.30
3.30
3.07
3.81
3.03
3.03
3.14
3.08
245
3-53
2.37
TOTAL "Kk"
9.93
13.84
50.59
29.74
8.48
12.03
148.59
28.02
2.88
15.96
13.33
22.78
111.79
38.95
11.30
20.62
31.43
4.89
14,84
2.37
4, 38
5.21
12.44
5.32
2.91
AVERAGE "K"
3.31
3.46
3.37
2.97
2,82
3.00
2.85
2.80
2.88
° s .
e
VNNMNMNNN NM NW
WO F ONO MANO OXNO
AW ONY OO CO FW AO
2.19
2.60
2.48
2.66
2.91
--- Page 18 ---
Table X
Belton Reservoir, Total Lengths, Weights and "K" Factors, June 1954 through May 1955.
(Weights given in pounds unless otherwise indicated. )
INCHES NUMBER WEIGHT RANGE TOTAL WEIGHT WEIGHT AVG. "K" FACTOR RANGE TOTAL "K" AVERAGE '"K"
Ameiurus natalis--yellow bullhead
i 85 gms 85 gems 85 gms 85 gms
Micropterus punctulatus~--Kentucky spotted bass
6 ems 8 pms 21 gms
El 7 gms 19 gms 186 gms
13 gms 29 ems 189 gms
0.2 0.2
4 4
0.2
0.5
1.6
0.2
0.5
0.8
8
Lepomis macrochirus--bluegill
1 gm 1 gm
3 gms 6 gms
28 gms 28 gms
28 gms 0.18
O«12 0.37
0.24 0.43
Pomoxis annularis--white crappie
6
4g
54
1
hy
8
2
27
37
9
4
10.23
106.26
131.19
2.70
10.34
21.40
9.87
87.98
122.78
31.69
14.03
3 gms
8 gms
e
°
2
63]
bh
St
=
ta
e
WWrrFWNMENEF OF
WNWOCTOT OA FOO
mn
bh
\o
0
B
nn
°
°
e
°
°
e
e
°
.
°
DArPIAUN VB 3 9
FPrFODWDOOOONF
ON OW OOO OA O%O
WwW FWwWwwh Ww FW PP
NO ODOOAFOADONA
AW ONOAONMONOFH
°
°
e
--- Page 19 ---
Table XI
Results of Creel Census, Belton Reservoir, Armistice Day, November ll, 1954.
SPECTES
Sunfish
Largemouth bass
European carp
METHOD
Still fishing
Trolling
BAIT USED
Minnows
Worms
Shrimp
Lures
Total fishermen--74 Total fish caught--62 Total hours fished--176.5
NUMBER OF FISH
22
2
56
2g
HOURS FISHED
7.0
61.0
11.0
140.5
26.0
49.5
hh 0
27 <0
26.0
FISH/MAN HOUR
O.4
0.2
0.6
0.02
0.3
0.2
Total fish/man hour--0.35
--- Page 20 ---
I
j a
;
7
|
\ IN
| wd is
/ ry
/ Hf
fe
q
ut
as
ae
iy
MEADOR GROVE
det
Arc
6
BELTON RESERVOIR | TEXAS
[%
CS INUNDATED Roaps
WS ROAD UNDER WATER AT
MF Loop CONTROL LEVEL
oes ts
yo _caTesvitce
TOP OF FLO
— \
OF CONSERVATION POOL EL. 569
OD CONTROL POOL EL.63/
——™,
/ FORT HOOD \.
NN
MILITARY RESERVATION
\
—,