TPWD 1973 F-6-R-20 #1522: Fisheries Investigations, Region 5-B: Job No. VIII, Fishery Management, Federal Aid Project No. F-6-R-20
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JOB PROGRESS REPORT
As required by
FEDERAL AID IN FISHERIES RESTORATION ACT
TEXAS
Federal Aid Project No. F-6-R-20
FISHERIES INVESTIGATIONS, REGION 5-B
Job No. VIII, Fishery Management
Project Leader; Rh. 1, McCabe
Clayton T. Garrison
ERECULLVeL Di Gee bor
Texas Parks and Wildlife Department
Austin, Texas
Lonnie Peters Robert J. Kemp, Director
Chief, Inland Fisheries Fish and Wildlife Division
May 10, 1973
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SUMMARY
Changes in tish harvest regulations were incorporated into the Southeast,
Oak Prairie, South Central Texas Hunting, Fishing and Trapping Proclamation
No. 0-3, 1972-73, which was approved by the Texas Parks and Wildlife Commis-
sion on July 7, 1972. The changes which affected Region 5-B included a re-
duction of the daily bag limit from fifteen (15) to ten (10) in the aggregate,
a minimum size limit of ten (10) inches, and a possession limit of twenty (20)
on largemouth, smallmouth or spotted black bass. The possession limit does
not include fish processed and stored at the fisherman's permanent residence.
The eleven (11) inch minimum size limit on channel catfish was removed and
an addition (iii) was made to section 7.02 (d) of the proclamation stating
"the daily bag limit on channel, blue, and flathead catfish is twenty-five (25)
in the aggregate. The possession limit is fifty (50) in the aggregate."
The wording of section 7.02 (d) was changed to clarify the boundaries of an
area with special regulations. Changes in "means and methods" of taking fishes
require that all trotlines set in public waters shall be redated at the end
of each ninety day period. In addition, "any trotline set in the public waters
of this state in violation of this proclamation shall be removed from the
waters thereof.'' The proclamation asserts that it is illegal to take catfish
in hoop nets, trammel nets, or gill nets of nonmetallic construction having
a mesh size not less than three inches square. It is also unlawful to possess
catfish on board any boat or vehicle while possessing a hoop net, gill net,
or trammel net.
Limited experimentation with granular 2,4-D ("Aqua-Kleen 20" by AMCHEM)
was conducted on Lake Corpus Christi to determine the effectiveness of the
chemical in controlling water stargrass infestations. The minimum effective
dosage rate utilized during the tests was 200 pounds per surface acre.
Further investigation in this area should be conducted by the statewide noxious
vegetation project.
In 1972 advanced young channel catfish were stocked in Lake Corpus Christi
(7,800 fish), Kleberg Park Lake (700 fish), and West Guth Park Lake (100 fish).
All fish were finclipped to provide future information on growth and sexual
development. Upon availability from State hatcheries, releases of advanced
young flathead catfish are recommended for Lake Corpus Christi and Alice City
Lake. The stocking of advanced young blue catfish is also recommended for
Alice City Lake.
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State Texas
Project No. F-6-R-20
Job No. VIIL
Period Covered:
P. S. OBJECTIVES:
JOB PROGRESS REPORT
Project Title: Fisheries Investigations
Region 5-B
Job Title: Fishery Management
January 1, 1972 to December 31, 1972
To situate fishery management practices in the waters of Region 5-B.
SEGMENT OBJECTIVES:
fish harvest regulations to the Texas Parks and Wild-
stocking ratios for newly constructed or renovated
waters, and in waters having established fish populations where
reproduction has been determined.
control of overabundant rough and/or game fish species.
need for rough fish removal by contract fishermen.
vegetation control needs.
public access needs.
1. To recommend
life Commission.
2. To recommend
insufficient
3. To recommend
4. To determine
5. To determine
6. To determine
PROCEDURES:
quarters through proper channels.
public at hearings in each of the regulatory counties of Region 5-B.
Proposed changes
observations recorded during previous surveys, were submitted to State head-
in fish harvest regulations, based on data and field
The changes were then presented to the
The
proposed changes, along with records of each hearing, were then submitted to
the Texas Parks and Wildlife Commission for final consideration. The follow-
ing public hearings were attended by F-6-R personnel:
PUBLIC
DATE TIME TOWN COUNTY ATTENDANCE
May 1, 1972 10:00 a.m. Rockport Aransas 25
May 1, 1972 2:00 p.m. Sinton San Patricio 0
May 1, 1972 8:00 p.m. Beeville Bee 0)
May 3, 1972 10:00 a.m. San Diego Duval ) 0
May 3, 1972 2:00 p.m. Alice Jim Wells 0
May 3, 1972 8:00 p.m. George West Live Oak 0
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There were no newly constructed or renovated waters in Region 5-B; there-
fore, no stocking ratio determinations were necessary. Objectives 2 through 6
of this study were fulfilled in conjunction with fisheries surveys conducted
on each major body of water having existing fish populations. The surveys
were conducted quarterly for the purpose of determining composition and
abundance of fish species and to determine supplementary stocking needs. The
waters surveyed included Lake Corpus Christi (Jim Wells, San Patricio, and
Live Oak Counties), Alice City Lake (Jim Wells County), Kleberg Park Lake
(Kleberg County), Lakeview Park Lake (Nueces County), and West Guth Park Lake
(Nueces County).
Five permanent sampling sites were established on Lake Corpus Christi
(Figure 1). Overnight gill netting, marginal seining, and water analyses were
conducted at all stations during each survey. Four gill netting stations were
chosen on Alice City Lake; however, due to a substantial decline in water
level, only three stations were accessible after the second survey. A map
of the lake showing the location of all sampling stations is given in Figure 2.
Due to the small size of Kleberg, West Guth, and Lakeview park lakes, no
permanent sampling stations were needed.
Experimental gill nets (l-inch to 34-inch mesh and 150 feet long) were
the primary means used for sampling adult game and rough fish populations.
Marginal seining was conducted with a 20-foot bag seine (4-inch mesh and 8 feet
deep) to determine spawning success and forage fish abundance. A 10-foot
otter trawl and an electroshocking device were used to supplement netting
and seining data. Water samples were taken with a Kemmerer water sampler
and analyzed with a Hach DR-EL Portable Engineer's Laboratory.
Gill net specimens were categorized by species and bulk weights were
taken. Individual weights and measurements were recorded on all game fish
and on a representative sample of rough fish. Game fish were also checked
for sexual development, stomach contents, and parasite infestation. Numbers
and weights of each species were totaled and a game fish-rough fish ratio
was calculated for each body of water sampled. In addition, average weights
were established for each species and average "K"' factors were computed on
all game fish species.
Seining collections were preserved in 10 per cent formalin in the field
and were later keyed and identified in the laboratory. Individuals within
each species were measured, separated by size group (juvenile, intermediate,
or adult), and counted.
All fish species encountered during Segment 20 are included ina
checklist (Table 1). Common and scientific names are in accord with those
found in Special Publication No. 6, A List of Common and Scientific Names
of Fishes from the United States and Canada (Third Edition), a publication
of the American Fisheries Society.
FINDINGS:
Fish Harvest Regulations
The Southeast, Oak Prairie, South Central Texas Hunting, Fishing, and
Trapping Proclamation No. 0-3, 1972-73 was approved by the Texas Parks and
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Figure 1. Lake Corpus Christi Sampling Stations.
LAKE
CORPUS CHRISTI
Dinero
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Switch
STATIONS
Hog Island
Green's Cove
Lagarto Creek
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Railroad Crossing
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e Seining
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athi
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Miles
Hwy. 359
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whye
Figure 2. Alice City Lake Sampling Stations
ALICE CITY
LAKE
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[ Texas Blvd.
660 Feet
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Table 1
Species Checklist
Common Name
Spotted gar
Longnose gar
Gizzard shad
Threadfin shad
Mexican tetra
| Carp
Goldfish
Golden shiner
Pugnose minnow
Red shiner
Bullhead minnow
Smallmouth buffalo
Channel catfish
Blue catfish
Black bullhead
Yellow bullhead
Flathead catfish
Tadpole madtom
Gulf killifish
Sheepshead minnow
Mosquitofish
Sailfin molly
Amazon molly
Tidewater silverside
White bass
Largemouth bass
Warmouth
Green sunfish
Redear sunfish
Bluegill
Redbreast sunfish
White crappie
Black crappie
Freshwater drum
Rio Grande perch
Mosambique tilapia
Striped mullet
Scientific Name
Lepisosteus oculatus
L. osseus
Dorosoma cepedianum
D. petenense
Astyanax mexicanus
Cyprinus carpio
Carassius auratus
Notemigonus crysoleucas
Opsopoeodua emiliae
Notropis lutrensis
Pimephales vigilax
Ictiobus bubalus
Ictalurus punctatus
I. furcatus
I. melas
I. natalis
Pylodictis olivarus
Noturus gyrinus
Fundulus grandis
Cyrinodon variegatus
Gambusia affinis
Poecilia latipinna
P. formosa
Menidia beryllina
Morone chrysops
Micropterus salmoides
Lepomis gulosus
L. cyanellus
L. microlophus
Tas
macrochirus
L. auritus
Pomoxis annularis
P. nigromaculatus
Aplodinotus grunniens
Cichlasoma cyanoguttatum
Tilapia mossambica
Mugil cephalus
po
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Wildlife Commission on July 7, 1972. Changes in the Proclamation which
affected Region 5-B fisheries included the following:
1. The daily bag limit on largemouth, smallmouth, or spotted black bass
was reduced from fifteen (15) to ten (10) in the aggregate.
2. <A minimum size limit of 10-inches in length was imposed on large-
mouth, smallmouth or spotted black bass.
3. A possession limit of twenty (20), which does not include fish
processed and stored at the fisherman's permanent residence, was
placed on largemouth, smallmouth and spotted black bass.
4. The eleven (11) inch size limit on channel catfish was removed.
5. The wording of section 7.02 (d) of the proclamation was changed
to clarify boundaries of an area affected by special regulations.
6. Exception number (iii) was added to section 7.02 (d) and states
that "the daily bag limit on channel, blue, and flathead catfish
is twenty-five (25) in the aggregate. The possession limit is
fifty (50) in the aggregate."
7. An addition to the Means and Methods (7.04) section of the Proc-
lamation asserts that "all trotlines that remain in public waters
shall be redated at the expiration of each ninety-day period.
Any trotline set in the public waters of this State in violation
of this proclamation shall be removed from the waters thereof."
8. Section 7.04 (g) was changed to make it illegal to take catfish
in hoop nets, trammel nets, or gill nets of nonmetallic construction
having a mesh size not less than three inches square.
9. Section 7.04 (g) makes it unlawful to possess catfish on board any
boat or vehicle while fishing with or possessing a hoop net, gill
net, or trammel net.
Lake Corpus Christi
(live Oak, Jim Wells, and San Patricio Counties)
Twenty experimental gill nets were set during the year. Netting results
were in keeping with those obtained during recent years. The catch-per-unit
effort was calculated for each survey and for the total annual yield (Table 2).
Netting results are given in Table 3, and a comparison of the game fish-rough
fish ratios obtained during each survey is presented in Figure 3.
Game fish represented 36.4 per cent by number and 26.12 per cent by
weight of the total fish netted. Channel and blue catfish accounted for 59.7
per cent by number and 73.8 per cent by weight of the game fish catch. Four
flathead catfish were taken during the quarterly surveys as opposed to none
during survey of the prior three year period. An additional small number of
flathead catfish were taken while assisting the U. S. Fish and Wildlife Service
)
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with an annual pesticide monitoring survey. White crappie, black crappie, and
white bass were present in satisfactory numbers. Smallmouth buffalo, fresh-
water drum, and gizzard shad constituted 90 per cent by number and 77 per cent
by weight of the rough fish taken in nets. Only three largemouth bass were
netted during the year; however, large numbers of 0-1 age group specimens were
captured during seining activities revealing a highly successful spawn.
An abundance of game and forage fishes were present in the seine catches
during each of the fisheries surveys. Game fish included largemouth bass,
white bass, white crappie, and sunfish species. The major forage species
seined were threadfin shad, gizzard shad, tidewater silversides, and grass
shrimp (Palemonetes sp.). A reproducing population of mosambique tilapia
were discovered with samples taken at the Hog Island and Lagarto Creek sein-
ing stations. No record of this species could be found in previous survey
data.
In December, the lake was stocked with 7,800 advanced young channel
catfish. All fish were finclipped to provide future information on growth
and sexual development.
Heavy infestations of water stargrass (Heterantherus sp.) occurred over
most of the lake's shoreline area during the early summer months. Experiments
with granular 2,4-D (Aqua-Kleen 20 by AMCHEM) were conducted to determine the
effectiveness of the chemical as a control measure. Distribution of the
chemical was accomplished with a Cyclone spreader and by hand broadcasting.
In July, three test plots were selected and treated at rates of 125, 145, and
187 pounds per acre,respectively. Poor results led to a second treatment in
August of all three areas at the same dosage rate. A visible reduction in
vegetation was noted, although the results were also unsatisfactory. In
September a fourth test plot was selected and treated at a rate of 200 pounds
per acre. This application resulted in a complete elimination of the star-
grass within the test area.
Water analyses results are given in Table 4. Water quality was acceptable
throughout the year. An unusually high turbidity reading (7500 JTU's) was
recorded during the December survey at Station One. Due to the wide range in
turbidity readings between the surface and bottom samples, it is probable
that a small amount of bottom sediment was picked up in the water sampler,
resulting in a high JTU reading.
Alice City Lake
(Jim Wells County)
A total of 13 experimental gill nets were utilized on Alice City Lake.
Sampling trips were made in March, July, September, and December of the year.
The relative abundance and weights of game fishes collected were greater
with rough fishes being considerably lower in 1972 than in previous years.
Netting results for the four surveys in 1972 indicated that the numbers and
weights of game fishes were rapidly declining (Figure 4). Game fish represent-
ed 60.2 per cent of the total number and 64.8 per cent of the total weight
of all fishes netted (Table 5).
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Table 5
Alice City Lake Netting Results, 1972
Species No. % No. Wt. % Wt. Ave. K. Ave. Wt.
Gizzard shad 152 23.64 61.1 14.55 .40
Carp 10 1.56 35.6 8.48 3.56
Goldfish 2 231 1.7 .40 .85
Golden shiner 14 2.18 2.3 255 . 16
Smallmouth buffalo 2 31 3.5 .83 1.75
Black bullhead 66 10.26 39.1 9.31 .59
Yellow bullhead 9 1.40 4.2 1.00 .47
Channel catfish * 38 5.91 54.6 13.01 1.89 1.44
Green sunfish * 4 .62 25 by 3.42 .13
Warmouth * 34 5.29 8.7 2.07 4.03 . 26
Bluegill * 47 7.31 5.7 1.36 4.12 sl2
Redear sunfish * 114 17.73 31.8 7.58 4.31 .28
Largemouth bass * 42 6.53 88.8 21.15 3.00 2.11
White crappie * 33 5.13 39.2 9.34 3.27 1.19
Black crappie * 75 11.66 42.6 10.15 3.40 .57
Rio Grande perch 1 .16 4 10 4
I i Ii
Total 643 100% 419.8 100%
Rough fish 256 39.8% 147.9 35.2%
Game fish 387 60.2% 271.9 64.8%
nn
* Denotes game fish species
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-15-
The rapid increase in game fish abundance may be correlated with lake
water level. At the time of the first survey in March, the water level was
near normal. During the next three surveys the water level dropped about
three feet to a minimum level in December. This decreased the surface area
of the lake from 100 to approximately 50 surface acres. This drawdown con-
centrated the fishes and may have allowed the game fishes to crop large num-
bers of the rough fishes. These larger game fishes may have also fed on
their offspring whose numbers dwindled in the seine samples taken in September
and December.
Sampling in December yielded an unusually high ratio of game fishes
comprising 86 per cent by number and 91 per cent by weight of all fishes
netted. Catches of white crappie and largemouth bass were large with 24
largemouth bass weighing 70 pounds being netted.
Seining activities in the first two surveys produced large numbers of
age class 0 largemouth bass. This spawning success was much higher than in
previous years. Forage fishes were fairly abundant during the first three
surveys with fish collections being sparse in December. Large numbers of
bluegill, pugnose minnow, gizzard and threadfin shad were collected. Numbers
and size of golden shiners declined greatly from 1971 surveys.
Sampling in July was supplemented by nighttime trawling and electrofish-
ing. Trawling efforts produced good numbers of game and rough fishes with
bluegill and redear sunfish being predominant. Trawling also produced the
first yellow bullhead collected at the lake as well as the only recapture
out of 2,000 finclipped advanced young channel catfish which had been stocked
in the lake in December, 1971. Electrofishing was also successful in
collecting game and rough fishes from shoreline areas with largemouth bass
and shad being predominant. Due to the low water levels, trawling and electro-
fishing were not attempted during later surveys.
Surface and bottom water samples were taken and analyzed during each
survey (Table 6). Results of the analyses were considered normal for the
lake and no significant changes in water quality were observed during the
year.
Kleberg Park Lake
(Kleberg County)
The lake is approximately five acres in size and receives its water
supply from nearby fields and range land. It has a maximum depth of about
eight feet with gradually sloping banks and a heavily silted bottom. The
lake has a high chloride content, total hardness, and turbidity. Widgeon
grass, water stargrass, water primrose, and filamentous algae are the major
plant species present. Small channel catfish and bluegill populations exist
in the lake while other game fish are lacking. The lake also supports several
fish species which are characteristically found in highly saline waters.
These include striped mullet, gulf killifish, and sheepshead minnows. In
December, the lake was stocked with 700 advanced young channel catfish in order
to supplement the game fish population.
--- Page 18 ---
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--- Page 19 ---
-l7-
Management surveys were conducted in March, July, September, and December.
Three experimental gill nets were set overnight during each survey. Only
eight game fish were netted during the year (Table 7). Of the total net
yield, only 14.3 per cent by number and 6.2 per cent by weight were game fish.
Gizzard shad dominated the rough fish catch by number and in weight. Other
rough fish netted included striped mullet, Rio Grande perch, black bullheads,
and one gulf killifish.
Marginal seining produced an abundance of forage in the first three
surveys of the year. However, forage was lacking during the December survey.
Bluegills were the only game fish species caught during seining activities.
Water analyses results are presented in Table 6. It was noted that the
lake level gradually dropped from a full level in March to about two feet be-
low normal in December. As the water volume decreased, the chloride content
and total hardness increased.
West Guth Park Lake
(Nueces County)
West Guth Park Lake is a shallow impoundment approximately one-half acre
in size and is utilized primarily by children of the surrounding locality.
It was surveyed in March and July of the year. Due to its small size, Lack of
water supply, and lack of spawning habitat, successful game fish reproduction
cannot be expected. With periodic stocking, the lake could provide a satis-
factory put, grow, and take fishery; therefore, in December it was stocked
with 100 advanced young channel catfish.
Netting efforts yielded a total of 19 fishes. Game fishes represented
58 per cent by number of the catch and 63 per cent by weight. The species
collected were channel catfish, black bullhead, and one goldfish (Table 8).
Seining activities produced large numbers of mosquitofish; however, no other
species were collected. Surface and bottom water samples were taken and
analyzed during each survey. Results were considered normal and are listed
in Table 6.
Lakeview Park Lake
(Nueces County)
Surveys at Lakeview Park Lake were undertaken in March and July, 1972.
A total of four experimental gill nets were utilized.
Netting surveys yielded only 17 fishes. The species collected were
largemouth bass, channel catfish, warmouth, and black bullhead. Game fish
comprised 65 per cent by number and 70 per cent by weight of all fishes
netted (Table 9). Several blue crabs (Callinectes sp.) were also taken from
the nets. Seining produced small numbers of largemouth bass, Mexican tetra,
and Rio Grande perch. Bluegills were present in fairly large numbers. Sur-
face and bottom water samples were taken during both surveys with results
(Table 6) which were considered normal for the lake.
None of the waters surveyed indicated a need for control of overabundant
rough and/or game fish species.
--- Page 20 ---
-18-
Table 7
Kleberg Park Lake Netting Results, 1972
Species No. ZNo. Wt. Wt. Ave K. Ave. Wt.
Gizzard shad 39 69.64 $27 29.96 514 |
Gulf killifish 1 1.79 .18 1.02 .18 |
Black bullhead 2 3.57 1.29 7.33 65
Channel catfish * 2 3.57 44 2.50 1.61 2
Bluegill * 6 10.72 . 66 3.75 4.25 ell
| Rio Grande perch 4 7.14 38 2.16 10
| Striped mullet 2 Bub? 9.37 53.28 4.69
Rough fish 48 85.7% 16.49 93 «7%
| Game fish 8 14.3% 1.10 6.3%
* Denotes game fish species
Table 8
West Guth Park Lake Netting Results, 1972
| Species No. No. - Wt. IWt. Ave K. Ave. Wt. |
| Goldfish 1 5.27 1.87 24.77 1.87
Channel catfish * 11 57.89 4.77 63.18 1.44 43 |
| Black bullhead 7 36.84 91 12.05 13 |
"Fotal 19 100% 7.55 100%
9 imueenmmaeemmanemeaanameanaueaiainaeuemuamnaaaianann deem
' Rough fish 8 42.1% 2.78 36. 8%
Game fish ll 57.9% 4.77 63.2% |
a6
ww
Denotes game fish species
--- Page 21 ---
-19-
Table 9
Lakeview Park Lake Netting Results, 1972
Channel catfish * 2 11.76 32 8.89 1.42 16
Black bullhead 5 29.42 85 23.61 .17
Warmouth * 4 23.53 57 15.83 4.21 14
Bluegill * 1 5.88 .09 2.50 4.63 .09
Largemouth bass * 4 23 55 1.54 42.78 2.59 .39 |
Rio Grande perch 1 5.88 23 6.39 23
i tc rt te nS meee hen tenements nett
Total 17 100%, 3.60 1007,
Rough fish 6 35.3% 1.08 30.0% |
Game fish 11 64.7% 2.52 70.0%
t
{
* Denotes game fish species
From data collected it was determined that not enough rough fish, small-
mouth buffalo, carp or freshwater drum, of commercial size, were present in
the project waters to warrant issuance of rough fish removal contracts to
contract fishermen.
No suitable sites for additional public access to project waters were
located during this segment.
RECOMMENDATIONS :
Survey data from recent years, as in 1972, indicates a poor flathead
population exists in Lake Corpus Christi. Supplementary stocking of 10,000
advanced young flathead catfish (6-8 inches) is recommended upon availability
from State hatcheries. It is also recommended that the statewide noxious
vegetation project conduct a survey to determine the extent of water stargrass
infestations and to determine an effective control measure if needed.
Stocking of advanced young (8-10 inches) flathead and blue catfish is
recommended for Alice City Lake. A stocking ratio of 15 blue and 20 flathead
catfish per surface acre could provide a control of the lake's rough fish
population and provide two additional species for the sports fisherman.
Due to its limited size, high chloride content, and the presence of
saltwater tolerant species, Kleberg Park should be considered as a candidate
lake for saltwater introduction studies.
West Guth Park Lake is heavily utilized by local fishermen and periodic
stocking of game fish species on a put, grow, and take basis is recommended.
\
--- Page 22 ---
-~20-
Lakeview Park Lake has a limited water supply, shallow depth, and poor
game fish reproduction. Lake overflow is extensive during periods of heavy
rainfall allowing the migration of species into and out of the lake. Under
these conditions, it is probable that established management practices would
provide little improvement to the fishery. It is therefore recommended that
management surveys be discontinued.
Prepared by Kenneth K. Sellers Approved by
Asst. Project Leader
Date May 10, 1973 Elgin M. C. Dietz
Regional Director for Inland Fisheries