TPWD 1961 F-4-R-8 #688: Fisheries Investigations and Surveys of the Waters of Region 4-B: Job No. B-29 Fisheries Reconnaissance
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TED LOWMAN
JOB COMPLETION REPORT
As Required by
FEDERAL AID IN FISHERIES RESTORATION ACT
Texas
Federal Aid Project No. Fe4-R-8
FISHERIES INVESTIGATIONS AND SURVEYS OF THE WATERS OF REGION 4-B
Job No. B-29 Fisheries Reconnaissance
Project Leader: Leonard Lamb
H. D. Dodgen
Executive Secretary
Texas Game and Fish Commission
Austin, Texas
Marion Toole Eugene A. Walker
D-J Coordinator Director, Program Planning
March 20, 1962
Elep
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ABSTRACT
Lake Arlington is a 2,200 acre water supply reservoir located on Village
Creek to provide municipal water for the City of Arlington. It was completed
in April 1957 and filled at once. Stocking was completed and the lake closed
to fishing until March 5, 1958.
Rough fish showed a slight rise in per cent of numbers but the per cent
of weight rose from 56.72 per cent in 1957-1958 to 80.99 per cent in! 1960-1961.
The majority of this increase was accredited to carpsucker which made up 79.75
per cent of the weight of fish taken by gill nets during 1960-1961.
Channel catfishwere the only game species to show improvement and this
change was offset by the drop in both per cent of number and weight shown by
largemouth bass and white crappie.
Fishing is hampered on Lake Arlington by excessive water skiing and speed
boat opérations.
Benbrook Lake is located on the Clear Fork of the Trinity River near Fort
Worth, Texas. The lake impounds 3,769 acres of water and was completed
September 29, 1952. A closed season was imposed during the first year.
The population was dominated by game fish during the early years of
impoundment as shown by the results of netting in 9953-1954 when largemouth
bass made up 84.77 per cent of the gill net catch.
The change from a game fish dominance to one by rough species has con-
tinued tather steadily as the netting in 1955-1956 showed spotted sucker to
make up 51.48 per cent of the rough fish total of 70.50 per cent. Gizzard
shad prédominated the 1960-1961 gill net catch with 80.50 per cent of the total
collections.
Benbrook Lake is another where the fisherman is troubled by excessive
water ski and speed boat operations. It is located so near Fort Worth that
non-fishing use is quite heavy.
Eagle Mountain Lake is located on the West Fort of the Trinity River
between Lake Worth and Lake Bridgeport. It covers 9,600f acres and was completed
in 1932 to serve as a water supply for the City of Fort Worth, Texas,
A fishery survey in 1955-1956 showed a predominance of game species with
white bass making up 48.99 per cent of the gill net catch, The game fish total
was 67.67 per cent. This condition did not prevail in 1958-1959 when a recheck
indicated that rough fish were the more numerous. The rough fish total of 78.51
per cent was made up largely of gar and gizzard shad with 41.43 per cent and
25.75 per cent respectively. The 1959-1960 netting provided a slight rough fish
predominance with 57.25 per cent of which gizzard shad comprised 33.59 per cent.
Net catches in 1960-1961 continue to show a rough fish trend with gizzard shad
accounting for 55.56 per cent of the total. Rough species amounted to 68.26 per
cent.
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Page 2 of Abstract.
The predominance of rough species is apparent but as yet there is not
sufficient evidence to support a recommendation for a chemical treatment,
Fort Parker Lake was congtyucted on the Navasota River, in Limestone County,
Texas, by the Civilian Conservation Corps. The dam was completed in 1938 to im-
pound 737 acres.
A survey was made in 1958 which indicated that an over population of gizzard
shad existed. An attempt was made to control the shad with a selective treatment
in November 1958. This application was made by helicopter using liquid rotenone
and was not successful.
In March 1960 another attempt to control the shad was made using Liquid
rotenone dispersed by boats using gravity flow treatment drums. This was a more
successful treatment but gill net checks showed that shad was still predominant
and a third shad control attempt was planned.
The third treatment was made in October 1960, when boats were again used
to distribute a higher concentration of liquid rotenone but with the addition of
an air boat to work the shallow water where outboards could not operate. This
shad kill was more successful but heavy rains resulted in reinfestation both from
above and below the lake,
Fort Parker continues to be a good crappie and channel catfish lake despite
the excessive shad population.
Possum Kingdom Lake is a multipurpose reservoir on the Brazos River. At
spillway level it impounds 19,991 acres of water.
A closed season was imposed during the first year of impoundment and for
the first five years fishing was excellent. The fishing declined until in 1953
many considered it a fished out lake.
Net checks between 1953 and 1956 revealed an abundance of gizzard shad and
an attempt was made to control this species by applying 2.5 per cent rotenone by
airplane. This application was made in August 1958 and was not ‘successful.
Gizzard shad made up 47.58 per cent of the net catches after this treatment and
a test was made using both liquid and powered rotenone. These tests were con-
ducted in the Rock Creek and Cédar Creek arms of the lake and were more success-
ful from the standpoint of the number and size of shad killed but had no lasting
effect as the shad moved in from the untreated areas until no change in popudation
could be noted. :
The netting attempted in 1960-1961 was hampered by bad weather and results
are far from complete. The majority of the fish taken were game fish with channel
catfish and bluegill sunfish the most numerous.
The reports of poor fishing together with the lack of recent data prompts
the recommendation that a resurvey be undertaken.
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Page 3 of Abstract
Lake Weatherford is a shallow lake covering about 1,800 acres that provides
municipal water for Weatherford, Texas. The dam was completed in 1957 and was
filled by heavy rains that broke the dams on several small farm and ranch ponds
thus liberating many adult rough and game fish into the lake.
The initial survey was made in 1957-1958 and the net collections showed 58.29
per cent rough; fish. Largemouth bass provided 12.75 per cent of the total catch
during this survey but were reduced to 1.07 per cent of the 1960-1961 net catch.
White crappie were of little importance in the gill net collections
during the 1957-1958 survey but increased to 58.61 per cent of the 1960-1961
total.
The catch per 100 feet of gill net showed little difference between the
surveys of 1957-1958 and the 1960-1961 but the pounds taken per 100 feet of gill
net increased by 2.54 pounds. The majority of this increase may be attributed
to the white crappie. This species showed a marked rise in both numbers taken
and pounds of fish per 100 feet of gill net.
Channel Catfish also showed an increase in both numbers and weight but not
to the extent as evidenced by white crappie.
Lake Worth was impounded in 1912 as a water supply for Fort Worth, Texas
and covered 5,400 acres at spillway level. It was the first of a series of three
lakes on the West Fork of the Trinity River.
The first survey of Lake Worth showed a predominance of game species in
the gill net catch. A total of 56.03 per cent of the catch were game fish with
white crappie accounting for 43.80 per cent. In the 1959-1960 netting game fish
made up 86.07 per cent with white crappie and white bass providing a majority
of this number.
The net collections in 1960-1961 were dominated by game species but not to
the extent that was observed in previous nettings. Only 54.17 per cent were
game fish. White crappie was the most numerous game fish but gizzard shad dominated
the catch as they provided 41.60 per cent of the number and 27.77 per cent of the
weight.
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JOB COMPLETION REPORT
State of TEXAS
Project No. F-4-R-8 Name: Fisheries Investigations and Surveys of
the Waters of Region 4-B
Job No. B-29 Title: Fisheries Reconnaissance.
Period Covered: November 1, 1960 - October 31, 1961
Objectives:
To conduct limited investigations to obtain current information concerning
gross changes in fishing conditions and factors influencing fish populations.
Techniques Used:
Certain previously surveyed lakes in Region 4-B were revisited and seine or
net checks made. Lakes Arlington, Benbrook, Eagle Mountain, Fincastle, Fort Parker,
Possum Kingdom, Weatherford and Worth were rechecked. These. data collected were re-
corded for examination and comparison with the results of previous surveys to pro-
vide a basis for determining if any change had occurred.
The results of these checks will be discussed later when each lake is treated
separately.
Findings:
Lake Arlington is located on Village Creek, in the eastern portion of the City
of Fort Worth, and covers about 2,200 acres. It was constructed by the City of
Arlington to serve as a water supply. The dam was completed in April 1957 and
filled before May 1, 1957. The Eagle Mountain State Fish Hatchery stocked this
lake with largemouth bass, channel catfish and sunfish, after which fishing was
prohibited until March 5, 1958.
The changes in the fish population since the original survey in 1957-1958
are significant but not unexpected (Tables 1 and 2). The perccent of rough fish
has risen from 50.68 to 56.24 but the weight shows a greater dominance by rough
species with 56.72 per cent in 1957-1958 and 80.99 per cent in 1960-61. River
carpsucker accounted for much of this change as this species made up 31.22 per
cent of the weight in the first survey, but provided 79.75 per cent of the total
weight in 1960-1961. The average weight of this species rose from 0.57 pounds
in 1957-58 to 2.06 pounds in 1960-61.
Channel catfish werethe only other species to show a marked increase. They
provided 1.52 per cent of the number and 2.24 per cent of the weight in the first
survey but rose to 21.88 per cent of the number and 10.65 per cent of the weight
in 1960-61.
Largemouth bass and white crappie made the most significant change from a
fishing standpoint. These species provided 20.72 and 18.92 per cent, respectively,
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of the number taken in the 1957-1958 survey but made up only 7.81 and 3.13 per cent
of the number taken in 1960-61. The loss in per cent of total weight was as marked
as that of per cent of number.
Black bullheads and carp disappeared from the catch in 1960-61 after providing
a substantial portion of the 1957-58 catch in both number and pounds.
There has been considerable fishing pressure on Lake Arlington but fishing
success has been hampered by excessive speedboat and water ski activities. The
location of this lake makes it accessible to a large number of people and the fee
charged for boating, by the City of Arlington, tends to encourage the speed and
pleasure boat use which discourages the fisherman.
Lake Benbrook is located on the Clear Fork of the Trinity River near Fort
Worth, Texas. It is a flood control and water conservation impoundment covering
3,769 acres at elevation 694 which is the top of the conservation pool. The dam
was closed September 29, 1952 but was not filled until 1957 because of low rainfall.
A closed season during the first year of impoundment was coupled with an inten-
sive stocking of largemouth bass, channel catfish and sunfish to produce a heavy game
fish population during the period of low water. This resulted in heavy catches of
small game fish during 1953-1954 when largemouth bass dominated the gill net collect
tions. Game fish accounted for 89.07 per cent of the entire catch with largemouth
bass accounting for 84.77 per cent (table 3).
The change from game fish dominance to a predominance of rough’: fish has
continued rather steadily. The 1955-1956 netting showed spotted sucker to make up
51.48 per cent of the total rough’ fish per centage which was 70.50. By 1959 the
rough species were dominated by gizzard shad with 62.67 per cent of the 69.13 total
rough fish per cent.
Gizzard shad continue to be the most numerous species in the 1960-1961 net
catch (table 4). They comprise 80.50 per cent of the total catch with spotted
suckers providing the remainder of the 81.35 per cent that were rough fish. Blue-
gill sunfish made up 10.17 per cent to lead the game species followed by white
crappie with 5.09 per cent.
The fishing on Benbrook Lake suffers during the summer months from competition
with water ski and speedboat operations. The fact that the lake is located very
near Fort Worth and is accessible for after work recreation makes it exceedingly popu-
lar with the boating public. Many of these users do not fish but their use of the
lake makes fishing difficult, if not impossible, during daylight hours in warm
weather.
Lake Eagle Mountain is the second in a chain of three lakes on the West Fork
of the Trinity River. The dam was completed in 1932 to impound 9,600 acres of
water to serve as a water supply for the City of Fort Worth, Texas.
A fishery survey made in 1955-1956 showed a game fish dominance in the net
catches with 67.67 per cent. White bass provided 48.99 per cent of the total catch.
The recheck made in 1958-1959 showed a predominance of rough fish in the net
catch with gar and gizzard shad making up 41.43 and 25.75 per cent, respectively,
of the rough fish total of 78.57 per cent.
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The 1959-1960 netting showed rough fish to be continuing in predominance but
only by a slight margin. The rough fish per cent was 57.25 which was composed
largely of gizzard shad and longnose gar with 33.59 and 17.76 per cent respectively.
The white bass returned to prominence in the catch with 25.19 per cent along with
white crappie which provided 11.46 per cent.
The 1960-1961 netting continued to show a rough fish dominance with spotted
gar, longnose gar and gizzard shad making up 68.26 per cent of the total. Gizzard
shad accounted for 55.56 per cent. The game species were rather evenly divided with
no species outstanding.
There is no doubt that rough fish occupy a large portion of the space in Eagle
Mountain Lake but the fact that this is a water supply tends to complicate any
remedial work planning. There is not sufficient evidence that a chemical treatment
would be successful at the present time and until satisfactory methods and equipment
can be developed such a treatment is not recommended.
Fincastle Lake is located on the headwaters of Catfish Creek in Henderson
County, Texas. A check of this lake was made during a stream survey on the Trinity
River and was found to have an excessive gizzard shad population. This indicated
a need for shad control and on May 20, 1958 an-application of liquid rotenone was
made. An estimated 36,960 shad weighing 16,592 pounds were killed in this 54-acre
lake,
Net checks made during a 12 month period took only three shad. These were
adult females weighing more than 16 ounces and each was gravid. There was consi-
derable evidence that the shad control was quite successful but net checks made -
during 1959-1960 showed gizzard shad to be the most numerous species making up
50.60 per cent of the catch. Ropgh fish accounted for 73.80 per cent of the total
catch. This predominance of rough fish prompted the decision to attempt a total
kill and restock with more desirable species.
This treatment was made on April 26, 1960 when rotenone liquid was applied
at a concentration of 1.0 ppm. The resukts of this treatment indicated that the
selective shad kill had removed all but a fraction of one per cent of the shad
but the resultant acceleration in spawning of this species had returned the
gizzard shad to numerical dominance within a very short time.
The net checks made since the lake was restocked indicate the total kill
attempt was successful on the gigzard shad but not on spotted gar, lake chubsucker,
yellow bullhead, black bullhead and sunfish. The above species were able to sur-
vive in the shallow heavily vegetated areas near the inflowing streams that feed
the lake. Black bullhead appears to be the dominant species now with 43.28 per
cent.followed by bluegill sunfish with 25.43 per cent.
Fort Parker State Park Lake is located on the Navasota River between Mexia
and Groesbeck, Limestone County, Texas. This lake was constructed in 1938 as a
Civilian Conservation Corps project.
A survey was made in 1958 which revealed that the shallow 737 acre lake was
over populated with gizzard shad. In 1958 an attempt was made to control the shad
by Spraying liquid rotenone from a helicopter, This treatment was not successful
and was followed in March 1960 by an attempt using boats. This treatment was more
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effective than the former but was far from successful. In October 1960 another
attempt at shad control was made using a higher concentration of rotenone and em-
ploying an air boat, tfo work the shallow water with a spray pump, in an effort to
redch all the shad. This treatment was much more successful but the exact degree
of success cannot be determined as the entire watershed could not be treated. This
fact coupled with the heavy rain that occurred immediately after the treatment re-
infested the lake with shad. Many shad were observed swimming up stream over the
dam which serves as a spillway.
The result of netting done in 1959-1960 does not indicate the true situation
as the nets used were of too large mesh to take the young of the year shad that were
very abundant in the kill (table 9). The per cent of total weight indicates that
the shad taken were of fair size. This lake continues to be a good crappie and
channel catfish lake as indicated by the data in table 10, but the netting did not
reveal the true status of these species since only a few were netted. Channel car-
fish provide much of the fishing in this lake and are of good size.
Possum Kingdom Lake was the first major impoundment on the Brazos River.
This multipurpose reservoir was completed in 1941 to be used for flood control,
hydroelectric power, irrigation and municipal uses. At spillway level 19,991 acres
of land are innundated to an average depth of 36.69 feet.
A closed season was imposed on this lake during the first year aftet impound-
ment. The bass that were stocked as fry, immediately after closure of the dam,,
were able to grow rapidly in this lake which filled to spillway level in a few weeks.
The fishing became phenominal and limit catches of large bass became the rule. This
condition persisted until the lake was about nine years old when the catches were
less satisfactory and by 1953 Possum Kingdom was considered to be fished out.
Net checks made during the next three years indicated an abundance of rough
fish of which gizzard shad was by far the more numerous species. Plans were made to
attempt control of shad by the application of 2.5 per cent synergized rotenone
liquid to the entire surface of the lake at the rate of 5.5 ounces per acre foot of
water. This application was made in August 1958 by use of airplanes. This treat-
ment was less than successful as shown by table 11. Gizzard shad made up 47.85 per
cent of the net catch in the survey that followed the shad kill (table 11). This
condition let to another attempt at shad control. This treatment was made with
boats that applied the liquidrotenone to the wdter by gravity flow together with
a treatment barge that mixed rotenone powder with water before applying the mix-
ture to the upper two feet of the lake. This treatment was restricted to the
Rock Creek and Cedar Creek arms to test the effectiveness of cove treatment. Net
checks before and after the cove treatments showed that fish moved into a treated
area within a short time and little effect could be noted.
Netting during 1960-1961 was not successful as bad weather hampered the work
during the time allocated to Possum Kfingdom Lake. A total of 28 fish were taken
of which 10 were channel catfish and 7 were bluegill sunfish (table 12).
Lake Weatherford was completed in 1957 to serve as a municipal water supply.
It is a rather shallow lake located on the Clear Fork of the Trinity Rover near
Weatherford, Texas. At spillway level this lake covers about 1,800 acres.
The watershed of Lake Weatherford included many small lakes and ponds that had
been constructed to provide water for livestock. Many of these overflowed or had
their dams broken by heavy rains soon after the completion of Lake Weatherford. This
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resulted in many rough fish being introduced into the lake along with some larger
bass, crappie and channel catfish.
The survey made in 1957-1958 showed 58.29 per cent of the net catch to be
rough fish (table 13). This is unusual in a new impoundment. The general rule is
for the game species to greatly out number the rough fish during the first year or
two. This condition frequently persists until the lake is three years of age when
the rough fish dominance begins to be apparent.
Largemouth bass were quite prominent in the catch of game fish during this
Survey as they provided 12.75 per cent of the catch. This was changed in the net
catch in 1960-1961 when bass provided only 1.07 per cent of the catch but white
crappie made up 58.61 per cent of the total (table 14).
The smaller numbers taken during the 1960-1961 netting is not to be taken as
an indication that the fish population is declining. An examination of the number
and pounds of fish taken per 100 feet of net shows that there is little difference i
in the number but the 1960-1961 netting provided an increase of 2.54 pounds of fish
per 100 feet of net. This increase is largely due to the rise in the catch of
white crappie. This species provided only 2.17 fish weighing 0.67 pounds per 100
feet of gill net during the 1957-1958 netting but rose to 12.11 fish weighing 4.07
pounds per 100 feet of gill net in 1960-1961.
Channel catfish also showed a sharp rise in the catch per 100 feet of net.
The 1957-1958 netting took 0.28 fish weighing 0.21 pounds, per each 100 feet of
net, as compared to 3.55 fish weighing 2.64 pounds taken in 1960-1961.
Lake Worth is the oldest of the lakes on the West Fork of the Trinity River.
It was impounded in 1912 to impound 5,400 acres of water for use as a municipal
water supply for Fort Worth, Texas. The level of Lake Worth is rather constant as
Eagle Mountain and Bridgeport lakes are located above it on the same stream.
The original survey of Lake Worth was made in 1955-1956 and game species made
up 56.03 per cent of the number and 34.78 per cent of the weight of all fish taken
by gill nets. The catch per 100 feet of net was 11.69 fish weighing 4.99 pounds.
White crappie made up the greater part of the catch as 43.80 per cent of the number
and 21.75 per cent of the weight were this species.
The 1959-1960 netting continued to show a predominance of game species with
86.07 per cent of the number and 49.27 per cent of the weight,.being made up of
game fish (table 15). The catch per 100 feet of gill net showed a rise in the
game fish catch over the netting of 1955-1956 with 21.00 fish weighing 9.85 pounds.
White crappie again lead in both numbers and weight. White bass were prominent in
the catch as they occupy second place in both numbers and weight.
In the 1960-1961 netting game fish still provided a majority but were less
dominant than in the previous samplings. Only 54.17 per cent of the number and 34.46
per cent of the weight were game species (table 16). The catch per 100 feet of gill
net showed a decided drop with 5.20 fish weighing 1.66 pounds taken. This was much
lower than the catch per 100 feet of net in the other net samplings. White crappie
failed to dominate the catch for the first time because gizzard shad provided 41.60
per cent of the number and 27.77 per cent of the weight in the 1960-1961 netting.
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Recommendations:
The results of the 1960-1961 Fincastle.Lake netting indicated a need for a
predator that would feed on the two species of bullheads. With this need in mind,
it was suggested that a heavy stocking of channel catfish be made together with
such flathead catfish as could be obtained not exceeding 200.
The lack of recent data together with the complaints on Possum Kingdom Lake
that few fish are being taken and minnows are scarce have prompted the thought
that a resurvey is needed.
Prepared by _Leonard D. Lamb Approved Laveen Laate
Project Leader oordinator
Date_ March 20, 1962
Regional Supervisor
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SL2°f 09*H-0L°2 79°0 OO'e BET ge°s 9S"? LT‘OT (ai ystjuns [1 Tsenyg
€0°S O2°7-S8°T LE°O os’o SS LO°E 97° T 69°T Z sseq YNowesie]
SS°T SO°T-SH°T 29°0 0s’*o Ofe €e°S 67°C 69°T 4 YsTyieo TeuuPey)
00°% o00°% 9T*O SZ°O 4 Of °T c9°O = S80 T xIeyons pejjodg
T9°T 06°T-O7'T 8S°6 GL°ES L1Té 87°08 TE*se TS'08 G6 ¥Peys prezZzty
yeu Fo yeu jo ( *wur) FYUSTOM ("sqT) us
eseisay o3uey 19°23 OOT 19°93 OOT yq8uetT jo qU3TOM 19g Jequny sotoods
wu wl ted spunog zed zequny e8e1sAy que. teg
EE
“1961-0961 ‘S3[Nser SuT}Jeu yoorqueg eyeY “Hy eTqeT
--- Page 15 ---
«Lli-
setoeds ysty y8nor seeoTpuyy
- - 8L°9% 02°92 < 00° OOT 76°EET OO'OOT TET STO]
e7°? OT’ E€-06°T LO°T ~ 00°€ 68T 00°” 9E°S = =GH*TT SI etddeis 93 TYM
OL°? OL°S €Z°O 0Z'0 OLZ 8B°0 8I°T 9L°0 T sseq Ynousesze7]
66°T O8°C-SZ2°T BT°e 09°9 €27% L8°TT O6°ST 61°SZ ce sseq 97 TUM
7S°T S8°T-OE'T OL*T 07° T GCE €€°9 87'S HE'S ZL ystyqeo Touueyp
17° 2:406°Z-29°T IL°0 09°0 0ZZ 79°Z yS°E 62°. € yleyonsdies 190ATy
OS*E OS *7-OL°? 87°0O 09°0 122 08‘ T T?'? 62°C € x0TeFFNq YANowWyT] eug
€6°T 07° S=07°T TZ°€ 08°8 LO?d L6°TI €0°9OT 6S°CE var] x¥PPYS PzeZZzTO
ELST 09°47 S9L 7L°8S L9°8L 9S *LT €Z 4183 ssousu07y
L7°0 —07°0 ony LL*T LEZ ES‘ é ¥1e3 peqjods
yeu Fo yeu jo ( * wur)y JUSTOM ("SqT) que)
aseisay oS8ury 32°23 OOL 22°F OOT y suet jo 1Yy3ToOM leq 1equnn setoedg
wu ii aed spunog zed szequnyn aseleay 4ueo Jteg
CC
"0961-6661 ‘S31Nse1: BuTIIeU UTeJUNOW oTSey oyeT °C STqQUL
--- Page 16 ---
-12-
setoeds ysty y8noi sojeotpuyy
eee
“ ~ IL°8 09°ZT - 00° 00T LS*€4 00°00T €9 STBIOL
——_—————-- rr )>$ eee
L7"Z = OEE -OT°Z 6Z°0 00°T QLT cere S7°T 76°L S etddez> 937UyM
c9°7 = 06" W-0F "#7 9T°O 08°0 9eT 98°T T8°oO St°9 7] ystjuns [][TsenTg
90°C = OL°?-09°T O£°O 08°0 (A0r4 LE°e LY°T SE°9 v sseq 37 TUM
00°? S2°C-SL'T aa) 0v7°O S72 16°? Le'l LT°€ cA sseq YInowss1e7
OS*T OS°*T-OS'T ae 02*O $8é OL'T ¥L°O 6S°T T UST eo peouelTT
19°T 06° 1-SE"T LL°0 08°0 €6¢ 18°8 78°€ ce"9 7] YSTs7Bo Touueyp
68°T 09°€-0H'T 08°? 0o°L OT? OT’ CE TO" vTI cc°cs cE xPePYS PpreZZzTH
SIZ 09°0 €18 S9*72 yL°OT §=9L*y € ¥183 9sousu0T
78°T 0Oo'T 97S 12°17 G2°6 76°L c ¥1e3 peqjodg
}eu Fo Jou FO (° wu) 343 TOM
eseisay o8ury 29°3 OOL 2925 OOT ya suet jo (*SqT) que)
Ae ET aed spunog Jed zequny = aSereAyY = quaD 3eq sq TOM leg Jequny setoedg
eee
“196T-096T ‘S3TNsez BuTIJ0U UTeIUNOW eTZeqy oyeY *g aTqeT
--- Page 17 ---
-13-
setoeds ysty y8nor seqeoTpuly
SSeS
ss 66° TT LL°02 A 00°OOT 68°€9% OO*OOT LS STPIOL
SSS
61°€ 6S°0O L8°0 €02 06°% 76°CT OT" 61 atddez> yortg
GZ°€ €Z°0 ZZ°0 SEZ 96°T 81'S 60°T S etdder. 97TYyM
SO*” S70 00°Z SET Le 88°6 €9°6 1 ystyuns []T3enTg
BS°€ 67°0O oS *T TOT £0" 79°OL 2z°L €€ ystTjuns 1Pvepey
os *€ 100 S0°0 ool Z1°0 ZE°O ZZ°O T yINowszeM
TE “2 S8°0 z8°0 77 60°L OL*ST = 76°E 8T — sseq YNouss1e]
6€°Z 6S ‘0 16°0 O€Z 68°77 06°21 = BE "YH 0z xPP2YTING MOTTOX
6S°Z €9°0 S6°0 972 77'S ZB°EL 86S YH 1Z xleyonsqnyg
10°% LL'E 0S ‘OT 661 Lyle €o'€s sSs*os 1EZ xPBYS plezzTH
Z9°0 BE" S6°% GLY 9S°9E 87°96 8622" HT S9 x1e3 pejjodg
yeu FO yeu Fo ( *uu) FUSTOM = (* ST) quaD
a8e1oAy 39°F OO1 3223 OOT yq8ueT Fo 2YUSTOM 13g requny setoeds
wa aed spunog ted zequny aseloAy Usd 13g
EEE
"0961-6661 ‘S31Nser BuT]JeU eye] eTAsvoUT, */ eTqeL
--- Page 18 ---
-14-
setoeds ysty y8nor seqeotputy
a
= = T9°9 OT*S?e - 00° O0T 6€°Z2T = 00’ OOT 6047 STPIOL
SS SSS
OL°% = OL°Z-OL*Z ss ZT 8€°0 SLI Z8°T en's tL" L etddeis youtg
06°% O° €-OL°% ST"O E70 OST Zee 78°7 S6°T 8 etddezs 93 Tym
19°Z = 0Z"9-ZZ°E Ov" T Z9°S SET 8I*1Z 26 °SZ €y'SZ vO1 ystyuns [1 ?T8entgq
E8°E 0% *7-0F'E S0°0 9T°O Ly LL‘0 76°O €L°O € ystyuns avapoy
72°S OS *Z-S6'T 8T°O €7°0 061 OL'Z oc € S6°T 8 sseq YyInowssieT
60°% OL°2-06'T Lo°T Sere LET EL*OT 7L°61 QT°ST Z9 xPBO4TING MOTTEX
77°% =—-09E-06'T 19°? LS°6 GOz 717° 6 L284 BZ ey LLI xPeoyTIng yoetg
S6°T S6°T-S6°T 90°0 ZE°0 OLT 86°0 Oz°T Ly 9 xieuUTYS UepToOD
09°% = 06°2-047°2 69°0 LS‘T OZ 7E°OT 99°21 60°L 6z xieyonsqnyo eye]
8Z°0 L1Z°O Of Zen 62°S 72° 1 G ¥1e3 peqjodg
Jou jo Jeu FO (* wu) FYUSTOM (’°SqT) U9
oseilsay asury 22°F OOT 12°F OOT yqsuet jo ' 4y8toMm log Jequny sotoeds
wha Wa zed spunog aed zequny eserzeAy jUed teg
SS EEE
"1961-0961 ‘S3Insear BuT}}eU eye] eTIsvoUT|, “gs eTqeL
--- Page 19 ---
-15-
sotoeds ysty ysnor seqeotpuly
eee
07°6 €E°LT - 00° OOT 79°78 00°O0OT 9ST STPIOL
eee
cO'” €E°S 902 ZO°EY T7'9€ = LL‘OE BY atdders 83 T4M
O€'0 00°2 TIT 8T°€ 69°Z 7S° 11 ST ystjuns [][T8enTg
81°0 9S°0 6471 L6°1 L£9°T IZ°€ c yanouwseM
70°T L9°T O1z 00° TT TE "6 19°6 ST sseq YyInowesszey
S0'0 ZZ°0 OST 190 zS°O 62'T z ¥PP2YTING MOTTE,
120 €£°0 €2Z CT°Z ze'T Z6°T € xpeeyTIng yortg
6£°0 7€°O 90€ 81°47 9G °€ 26°T € ystj3e9 Teuueyy
71°0 €€°T 621 CS‘ TE*T 69°L ZL xOTBJJNG YJnowT] Pug
ET'Z BL" 902 8S°7 Il°6T LE°LZ ey xPpeys piezzty
16°0 LL°O 20% 9L°6 97°83 84° 4 L ¥1e3 peqjods
eu jo Jeu 50 (wu) FUSTOM (°SqT) qus_5
322J OOT 37923 (DOT. ya Suet jo 243 TOM ied iequny satoedg
tod spunog zed izequny ese12aAy 4ued iteg
EES
"0961-6561 ‘s3[Nsez SuTz}eUu eye] Aeyzeg YZ0q +6 OTGEL
--- Page 20 ---
-16-
setoeds ysTy ysnor sajPoTpuly
= - O€ °ET OS *ST - 00° OOT 18°6ZL 00°*OOT €6 STPIOL
8s9°€ = OS*7-09°% 76°72 LT°€ 9TZ 80°C? cO°LT €v° 0? 61 atddez. o7TyM
SE°7 09°7-OT*# 90°0 €£°O Sel 97°0 LE*O GT°? Zz ystjuns T]TsenTg
97°7 O00°S-S8’°E €Z°O £9°0 CST ELT BE°T Of? v7] yINowseM
8S°S = OO'E-SE°S 06°0O OS*T LTZ L£L°9 ov's 89°6 6 sseq YINowsesi1e7]
46°2 OL 7-Se°? OL*O LT°T 96T TES O° ec°L L xPP2YTTNG MOTTO,
76° T Oc 7-EE TT 7B°E 00°e eT te 78°87 ZOE? = GE“ 6T 8T ystyqeo Teuueyg
O2*S = 0S H-GO°T 69°T Os’*e€ ET? L9°@T IT‘OT 89°22 1Z xPePUS PIeZZTIN
76°G 91°? 094 vc? LO*LT = BB“ ET €1 4183 peqjodg
you Fo Jou FO (*wu) qUSTOM C’°SqT) ue
eSerlsay esuey 29°F OOl 2925 OOT yq suet jo 2YSTOM jeg iequnyn sotoedg
wu wa aed spunog zed szequny a3eloAy que. tog
oO ce eo eee nw
“1961-0961 ‘SS3INser BuTAJeU SYST A9eyIe_ 340g ‘OL PTIPL
--- Page 21 ---
-17-
setoeds ysty ysnol sa .eoTputy,
- = 87°07 ZO" EZ - 00°OOT . LZ°060Z 00°O0OT 67€*Z STO]
Ly°Z = OO" E-OT°Z% S0’0 90°0 87 SZ°0 BI°s 97°0 9 wnaq
S7°% = OS *Z-07°Z Z0°O ZL €0°O 9S°0 60°0 4 etddeis yorlg
T9°Z = OVE -06°T 87°O 6€°T O8T €f°7 6L°84% S0°9 cyt atdderzs 37 TyM
06°Z 06°2-06°2 10°0 O9T Z0°0O Se°O 70°0O T ystyuns 1vesu0y
O8°€ O8°€-08'E 10'0O O€T T0°0 0z°0 70°O T ystyuns ATTeqMoT Tex
00°7 O00°S-O1'E 6£°0O S9°T TEL 06°T ZL°6E = STL BOT ystyuns [1 T3enTg
oz*€ b0°-0€°T 8T°O 99°0 9ST 98°0 S6°LT =S8°z L9 ystjuns i1vepey
OO°E O00°E-00°€ 10'0 €0°O OST 70°0 88°0 E10 € yINnowseM
S6°l O1°2%-08'T 10°0 z0°0O OvZ 80°0 29° T 60°0O Z sseq peqjods
€€°Z = OL*E-06'T S7°0 8S °0 882 ez 82°99 = 1S *Z 6S sseq yInowses1e7]
€7°Z = OZ E-SH°Z Zo 1 T€°Z 612 S6°9 77°77 =SO'OT 9EZ sseq 32 TUM
ZL°T = OW Z-OTTT Bas 97°T OSE IT°Il 61°TET 67°S 671 Ysty}eo Teuuey)
€6°% O7°%-07°7 80°0 S0'0 787 T7°0 LS°8 1Z'0 S ¥dze9
LS°2 O€°€-08"T T7°T Te*T €9Z 68°9 60°71 OL°S vET xreyonsdies 19ATY
8Z°E =—07 "7-06 °S 69°0O 0z°0 EZE 6£°€ T6°OL 68°O TZ = xOTBFFNG YINowy T eug
06'Il OO°E=ST°T 78°C ZO°ItT O€Z 67°82 €7°S6S S8°Ly 71ST xPeYs plezZZ1O
76°9 77°Z 069 G8°ee LS*LoL SL°6 622 ¥183 asousu0y
S70 0Z'0 9476 gI°e." yS'S S80 02 x13 feqqodg
aselsaAy asury jeu jo jeu jo c¢° ww) TUSTOM (SqT) queg
wn wn 3®9F OOT 38°F OOT yq3ueT jo 1YSTOM tag iequnn satoedg
jad spunog jed zequny oeser0ay judd 138g
"6S61L-SS6L ‘Sa[Nser BuTqJoOU oyeT wWopsuTy wnssog
“TT eT9PL
--- Page 22 ---
-(3~
setoeds ysty ysnoi sejzeotpuyy
ee
- - Z9°T 08*z - 00°00T EZ°9T 00'OOT gz STPRIOL
eee
OL*% =6OL°e 70°0O OT‘O Ost 91°Z S€°O }8=6LS*E T atddeag 9314M
TL'E = 09° 7-S6°Z ST*O oL°O LET 7Z°6 OS*l o00°Sz l ystyuns T][TS8enTg
06°€ 06°€-06°E 90°0 0Z°0 CST Bs°€ €9°O = HTL z ystjuns reepey
orz oT*z OT*O OT‘O 08z 91°9 OO°I LS°E T sseq YNowes1e7
ZO°S = OE *Z-SL'T Z1°O 0Z°0 CE 60°L ST'l TL z - sseq poqjodg
00°% 00°? 90°0 OT‘O S27 76°€ 79°O LSE T sseq 37 TUM
ZS°Il = S6* T-OT'T 1L°O 00°T 692 66°Eh "I'L ZL°SE OT ystyieo Teuueyy
Of°Z of'z Z1°O OT‘O 062 79°L 77° = LG*E T yieyonsdies aaaTy
06°Il S6*I-S8"T ILO 0Z°0 SEZ ZL°9 60°T IZ z xPPYS PIPZZIQ
ST°0 oT"o 099 81°6 67°T LSE T ¥1e3 ~esou 8u07]
Jeu jo Jou FO (wu) 7USTOM (°SqT) que
aseisay asuey 22°F OOT 2223 OOL yqS8uet jo 3U3TOM leg Zequny setoedg
in wu aed spunog aed zequny ase1say qued t3eg
rr
*196T-0961 ‘S3[Nser SuTZJeU SyeY wopSuTy wNssog ZT Teqey
--- Page 23 ---
-{9-
setoeds ysty ysnoi saqvotputy
_ ese Ce pe
- - TS*L 9c‘ 6T = 00°*OoT 62°71 OO0°OOT 67S STPIOL
a SSSSFSSSSSSSSSSSSSSSeSeeSSSSEEEEeeee
17°C 06°Z-OL°T L£9°0O LVS 6LT 68°8 SO°6T ‘62°TT c9 etddeis 37 TYM
SL°Y 00°S-08°E 6S°0 9° Cel 06°L €6°9T Of °ET €L ystjuns TT TSenTg
6L°€ 00°S-c7°€ LT‘O €S°O SST LO°? L8° €L°? ST YstTjuns 1Peepey
10°O 70°0 Sct €1‘O L£é°0 8T°o T ystyuns w9ex9
19°? 07° €-OS‘*T T?7°T 97°C LIZ LL°8T cC' OV GL°SCT OL sseq YyInouses1e7]
6E°?C OL°?-S0°% vT'O 72°O CCS L8°T 00° 8c'T L ¥PBSUTING MOTTOR
69°C 08*2-SO"T 76°T 8c" 7 11é O8°Sé 82°SS CCS cel *PPOUTING 4oriTg
T9°T S6°1T-S#'T 12°0 8c2°0 { 88¢ 9L°? c6°S 97° 1 8 ystgieo Teuueyp
OT‘e 00°E-29'°? €£°O 9S°0 672 Ty" S7"6 c6 °C OT ¥d1e9
Lo‘? OT*€-06°T LY7°0O 78°0O LT¢é €2°9 9E°ET LE°v ve xLeyoNsdivs TIATY
73° T 00°S-O€°T LS°T O€'S 70¢ L6°0% €6° 7 OS*LZe TST *PePYS Pprzezzty)
Jou Fo Jou jo (wu) JUSTOM (°SqdT) ay)
eseisay e8uey >> 3885 OOT 19°F OOL y33ueT jo 1Y3TOM 19g Jequny setoedg
was wu aed spunog ted szequny e8ersay queso 130g
nn eee nn
“SS6T-LS6T ‘SI{nsea BuT}Jeu pszojzzeyzVoM eye “ET eTqeL
--- Page 24 ---
-20-
setoeds ysty y8noi saq.eotpuyy,
7 = SO°OT L9°0% - 00° OOT 87°06 00°OOT 98T STBIOL
rt el es
€T°? OO°€-09°T LO°” TL’ 2@T T6T 1S Ov S9°9E =09°8S 60T etdders 93TYM
LT°€ 00°-06°Z T7°0O €€°7? 08 40°” 89° 6c° TT 1? ystjuns [][T8enTg
O8°T O8°T-O8'T 9T*O 22°O 09¢ BS°T C91 80°T Z sseq YInouses1e7
O8°T O02°2-0S*T 70°O €£°O 6ST T?°0 LE‘O 19°T € ¥PPOYTING xorg
Ov7*T SO°%-SO'T 79°C cG°e £6¢ 92° 9¢ 9L°ES = TZ LT cE YsTyqeo Touueyp
cE*S «OZ *E-08°T €38°0 08°0O 9Le 9Z°8 87°L OL°E L ¥diep
OL°? O2°E-0€°? LL°1 68°0 e1E LS°LT 06°ST Of ' + 8 xleyonsdies T9ATY
89°T 06°T-0S°T €1°O 77°0 £02 vErT T2°T GT°? Vv) ¥PeYS P1eZZzTH
Jou jo you jo (ww) JUSTOM (*SqT) que.
aseieay o8uey 3225 OOT 32°F OOT yq8ueT jo 2USTOM Jeg iequny sotoeds
iii wu ied spunog jed rzequny aseisay que. 10g
meee ee
“196T-096T “S31NSer BuTIJOEU PpAOJIEYIeSMm OyeY °~HT oTQGeL
--- Page 25 ---
2?1=
setoeds ysty usnor soqeoTpUuTy
cn
- 08 *2T 07°77 - 00°00T 70°79 00°00T Z21 ST BIOL
a
GS°Z 08*Z-0€°Z 9T'0 070 S61 97° 1 18°0 79°T z unig
6S°Z Ov'E-02°2 el’ Og* TT T61 86°9E S9°EZ =—-9E "BH 6S | atdder1s ea TUM
71°? 08°7-09°€ 77°0 08° SET Ov'€ BIZ se'L 6 ysittguns [1 T3entg
09°% 09°% Il‘0 0Z°0 O1z €8°0 ES*0 z8°0 T sseq peqjods
LZ°Z 09°%-00'% L8°Z O7'S 02Z 17° 2 GE"yL E1°% LZ sseq 37 TUM
zZG°l OL*T-O€'T OL*T 08" 682 ZE*ET ES°s Berl 6 ystyqeo TouueYyy
0S'z 0S*z 60°0 02°0 00z 69°0 yO = z8'0 I ¥die9
oS'% oS*z 0z°0 0Z°0 09Z 9S°T 00°T z8°0 I OT PFINq YINoWTT] eUS
98° 0%°Z-0S°T 8€°0 ov7*T 8sl oo°€ Z6°1 EL°S L xPeys plezZzTH
0S *O 0z°0 029 68°€ 677%) = Z8°O T x1e3 ssousu0y
Z9°T 00*T 06% 99°ZT II's ol’ c xie3 pejjodg
Jeu Fo Jeu Jo (*Um) Jystom =" SAT)
eseicay osuey 32°F OOT 32°95 OOT yq3ueT jo 1Y3TOM leg requny sotoedg
wu was aed spunog ged zoquny eS3eieAy 4usd Jog
"0961-6561 ‘STNse1 Sut Jeu YIAOM OAPT “ST PTIPL
--- Page 26 ---
-22-
setoeds ystz y8nor seqeotpury
a ee a ge CT ts Teel han
: = TL* 09*6 = 00° OOT SS*€Z 00°OOT 8Y STBIOL
ORR a ne
LS*Z OS*E€-oO1°Z 68°0 00°e eLT 18°8T Cy 92° TE ST etdderzs o3T4yM
€2°7 09°7-09°E L£Z°0O 0¢*T cET 69°S VET OS *CT 9 ystTjuns []T1senTg
O2*e O¢'°? OT*o 02°0 022 €1°? 0S*O 80°? T sseq 3 TUM
S6°T S6°T €T°O 02°0 OSZz 08° 99°0 80°? T sseq YJnoweds1e7
GSS°*T S8°I-SE°T L£2°O 09°0 9€~ ELS SET SZ’9 € 4stzzeo Teuueygp
f6°T O0°E-SO°T T€°T 00°% 861 LL°L2 7S °9 L9° TY 02 xPBYS prezztg
OT 020 06 B9°6Z 66°9 = 80°Z T ¥1e3 esousu0T
7E°O 0z°0 Ost 6e*L HLT 80°Z I ¥183 poeqjodg
yeu jo you Fo (wu) JUSTOM (Sq) qus5
eseiesay aSury 29°F OOT 39°F OOL yqsueT jo VYESTOM leg Jequny satoedg
wa wa aed spunog Jed zequny eseieAy yued tag
“T96T-O96T “SITNser SutZIEU YII0M syeT ‘OT ater