ML20052G927
ML20052G927 | |
Person / Time | |
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Site: | Arkansas Nuclear |
Issue date: | 12/31/1981 |
From: | ARKANSAS POWER & LIGHT CO. |
To: | |
Shared Package | |
ML20052G922 | List: |
References | |
NUDOCS 8205190161 | |
Download: ML20052G927 (400) | |
Text
{{#Wiki_filter:Jr , m aJ 4._ + m 4 ,+J,.-- r A 4m A p --. A m. ANNUAL ENVIRONMENTAL MONITORING REPORT ARKANSAS NUCLEAR ONE UNITS 1 & 2 DOCKET NOS. 50-313 & 368 LICENSE NOS. DPR-51 & NPF-6 I
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TABLE OF CONTENTS PAGE i i Dardanelle Reservoir Fisheries Survey 1 Dardanelle Reservoir Illinois Bayou Embayment Survey 234 Report on Larval Fish Entrainment at ANO 312 A Summary of Fish Impingement Monitoring at AN0 343 Report of Thermal Impact Evaluation After ANO Unit-1 Shutdown 368 1981. Annual Environmental Radiological Monitoring Report for AN0-1 & ANO-2 384 ANO Monthly Chemical Usage 450 Summary of RCS Analysis of I-131 452 i Summary of Environmental Non-compliances and Changes 459 Attachment 1 Report of Remote Sensing and Vegetation Ground Truth Program
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l DARDANELLE RESERV0IR FISHERIES SURVEY PROJECT NO. 873 PROGRESS REPORT NO. 14-BUFORD TATUM Student Assistants Michael Kepesky Gary Riordan Donald Clover Ronald Duvall c . >
TABLE OF CONTENTS Figure 1 Kap of Lake and Sampling Locations GILL NET Table 1 Total Number of Fish Caught per Station by Date and for the Year Table 2 Total weight in Founds per Station by Date and for the Year Table 3 Number of Species by Station Table 4 Weight in Pounds of Species by Station Table 5 Species Numbers of Fish per Date by Station THAMMEL NET Table 6 Total Number of Fish Caught per Station by Date and for the Year Table 7 Total Weight in Founds per Station by Date Table 8 Number of Sp!cies by Station Table 9 weight in Founds of Species by Station Table 10 -- Species Numbers of Fish per Date by Station COMBINED GILL AND TMAMMEL NETS Table 11 Number of Species by Station Table 12 weight of Species by Station OMAP NET Table 13 Total Number of Fish Caught per Station by Date and for the Year Table 14 Total weight in Founds per Station by Date Table 15 number of Species by Station Table 16 weight in Founds of Species by Station . Table 17 Species Numbers of Fish per Date by Station
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7 .. - - - TABLE OF CONTENTS ( Continued) METER NET Table 18 Number of Fish per Station by Date and for the Year Table 19 Species Numbers of Fish per Station Figure 2 Bar Chart Comparison of all Fish per Replicate Table 20 Abnormalities by Species and Station ' Table 21 Species Numbers of Fish per Date by Station ' MID WATER TRAWL Table 22 Number of Fish per Station by Date and for the Year Table 23 Species Numbers per Station Figure 3 Bar Chart Comparison of all Fish per Replicate Table 24 Abnormalities by Species and Station Table 25 Species Numbers of Fish per Date by Station FISH BAG SEINE Table 26 Number of Fish per Station by Date and for the Year Table 27 Weight in Grams of Fish per Station by Date and for the Year Table 28 Species numbers per Station Table 'c9 Species Weight in Grams per Station Figure 4 l Bar Chart Comparison of all Fish per Replicate Table 30 Abnormalities by Species and Station Table 31 Species fiumbers of Fish per Date by Station . _-- w
, ~ ~ - - -- . _- ; . - TABLE OF COUTEETS (Continued) ROTE!:ONE Table 32 Species Numbers and Weights per Station Table 33 Number of Fish per acre by Station i Figure 5 Bar Chart Comparison of Numbers of Gizzard and Threadfin Shad Figure 6 Bar Chart Comparison of Weights in Pounds of - Gizzard and Threadfin Shad PHYSICAL WATER RUALITY Table 34 Daily average of Dissolved Oxygen and niater Temperature and Other Parameters by Station Table 35 Monthly Average Dissolved oxygen, Water Temperature, Secci,hmbient Air Temperature,and Lake Level by Station AGE AND GROWTH Table 36 Age and Growth Data for Blue catfish Figures 7-10 Line Graph of Age and Growth of Blue Catfish by Station Table 37 Age and Growth Data for Channel Catfish Figures 11-14 Line Graph of Age and Growth of Channel Catfish by Station Table 38 Age and Growth Data for Flathead Catfish Figures 15-18 Line Graph of Age and Growth of Flathead Catfish Table 39 Age and Growth Data for Freshwater Drum Figures 19-22 Line Graph of Age and Growth of Freshwater Drum Table 40 Age and Growth Data for Largemouth Bass Figures 23-25 Line Graph of age und Growth of Largemouth Bass Table 41 A6 e and Growth Data for White Bass Figures 26-28 Line Graph of Age und Growth of White Bass Table 42 Age and Growth Data for White Crappie Figures 29-31 Line Graph of Age and Growth of White Crapple , w . .
I
'A
SUMMARY
OF.THE DARDANELLE'RESERV0IR~ FISHERY SURVEY-FOR JANUARY 1 THROUGH DECEMBER 31, 1981-Review of the data generated by this program indicates-that the-operation of Arkansas Nuclear One is not h'aving a'significant impact on the _ fishery of Dardanelle Reservoir. The survey characterizes the fish population in the reservoir _by use of the following sampling gear and methods: A. .Rotenone B. Meter Net C. Mid-water Trawl D. Shoreline Seine E. Trap Net F. Gill Net G. Trammel Net H. Physical Water Quality I. Age and Growth Four sample stations are used. Backwater Area A is located upstream of possible plant influence and is used as the control station. The other three stations, Intake Area B, Discharge Area C and Channel Area D are located in areas where potential plant impact would'be expected to occur. D 1
E-l 1 A general characterization of the fishery in the reservoir is that it is highly variable. However, there does not appear to be a major shift in species diversity or relative density over the eight year sample period, 1974 through 1981. Since many fish species move into the shallows at night, an effective method of fish population estimation has been the use of rotenone in a representative section of these areas. This part of the fishery survey is conducted under the supervision of the Arkansas Game and Fish Commission on a yearly basis, usually in September. Two areas are sampled, the Backwater (control) and the Discharge. There appears to be a general increase in the 1981 fish population over 1980. The data for the eight year sample period shows the number and weight of fish per acre to be varied. The lowest population was found to be in 1975 with 1755 in number per acre and 290 pounds per acre. The highest population occurred the next year, 1976, with 9414 in number and 741 pounds. The eight year average number and weight per acre is 5846 number and 572 pounds. In 1981, there were 6029 number per acre and 605 pounds per acre. ( Examination of the commercial / sport and forage fish species in the reservoir reveals the Gizzard Shad, Dorosoma cepedianum (LeSueur) and Threadfin Shad, Dorosoma petenense (Gunther) to be the most plentiful species. They are followed in number by the Sunfish species, commonly 2 y .- v --+
referred to as bream, Freshwater Drum, Aplodinotus grunniens (Rafinesque) and Channel Catfish, Ictalurus punctatus (Rafinesque). The other species occur in much lessor numbers. The general yearly reservoir fish population trends, represented by number per acre, obtained from tra rotenone survey data (Figure 1), indicate a similar trend between the Backwater and Discharge until 1978 at which time they become diametrically opposed to each other. The primary difference is a fluctuation in the Shad population, especially the Gizzard Shad. Also, the bream species, largemouth Bass, Micropterus salmoides (Lacepede) and Drum contributed to the increase in total fish in the Discharge in 1978. The general fish population trend throughout the sample areas indicates yearly fluctuations due to natural variation. Some species of fish seem to prefer one area more than another. Largemouth Bass, bream and Channel Catfish occur in greater numbers in the Discharge, while Threadfin Shad, Blue Catfish, Ictalurus furcatus (LeSueur), Flathead Catfish, Pylodictis olivaris (Rafinesque), White Bass, Roccus chrysops (Rafinesque), Striped Bass, Roccus saxatilis (Walbaum) and White Crappie, Pomoxis annularis (Rafinesque) occur in greater numbers in the Backwater. The other species do not appear to prefer any one area over the other. Utilization of meter net, mid-water trawl and shoreline seine sampling gear aids in the detection of fish spawning activity and 3
survival of the larval fish. A review of the data reveals that the gear is selective for the Shad species, White Bass, Bluegill Sunfish, Lepomis macrochirus (Rafinesque) and White Crappie. Spawning activity is inpossible to detect for the other species. Clupeidae usually spawn early in May through June in all areas including the Discharge. This is true whether the Discharge water-temperature is slightly elevated due to plant operation or if the plant is off-line during the spawning season. Only occassional small peaks are observed in July, August and September. The average water temperature at the beginning of spawning ranged from 20 C to 22 C between the four sample areas. Meter net data indicates a decrease in fish spawned in 1976 (Figure 2). However, mid-water trawl (Figure 3) and shoreline seine data (Figure 4) provide evidence to the contrary. In fact, there was a dramatic increase in the larval fish population, primarily due to Clupeidae. Rotenone data also indicates a large increase in adult fish numbers, namely Clupeidae. White Bass spawn is more difficult to detect due to the very small numbers in the samples. Spawning probably occurs in early April but has been observed as late as mid-June. The average water temperature during spawning ranges from 14 to 21 C. 4
No larval White Bass were detected in the 1979 through 1980 meter net samples. Other sample gear did_ detect a few individuals, but there appears to be a general decrease in the White Bass population in the past several years. However, this does not appear to be an abnormal occurrance in the reservoir and is probably a natural trend (Figure 23). The Crappie species appear to spawn in mid-April through May in an average water temperature range of 19 to 24 C. Occasional small peaks are observed in June, July and August. The bream species usually spawn at a later date. Spawning begins late in May and continues into August with an average water temperature range of 24 to 28 C. At no time in the eight year sample period has any species been observed to spawn in March. Therefore, beginning sampling in March proves to be of no value. The Backwater usually yields the greatest number of spawned fish and consists primarily of the Clupeidae species. On two occasions, 1976 and 1980, the Channel was obsered to yield an unusually large population'of larval Clupeidae (Figures 2 and 4). l 4 Mid-water trawl data is used to estimate the survival of the larval fish. It should be noted, however, that this method is not without 5
discrepancies (Table 1). There have been instances where there are nearly as many larval fish caught in the mid-water trawl as in the meter net or there were more fish in the mid-water trawl samples. This occurrance is notable in 1976, 1977 and 1981 for all four sample areas. 1 Generally, no more than 5 to 10% of the larval fish reach maturity in any
- of the areas. The Discharge area does seem to have the highest survival percentage from 1975 through 1981. Operation of Arkansas Nuclear One may be exerting a beneficial influence in this respect.
Trap nets usually yield fewer fish per sample effort. The data indicates trends different from the gill and trammel net data (Figures 5 through 7). The Backwater and Channel yield fewer fish and are observed to follow a trend consistent with each other over the eight sample years. The Intake and Discharge are highly variable. Very large numbers of Threadfin Shad and White Crappie account for the peaks observed in 1975 and 1977 data and Threadfin Shad and bream account for the peak in 1981 data (Figure 5). Gill and trammel nets indicate yearly variability and somewhat different fish population trends between the two types of sampling gear. However, species diversity and density are consistent between the two. r The major difference between the three types of sampling gear is the species selectivity they exhibit. The trap net selects most heavily for 1 Threadfin Shad and bream. This is most likely due to the smaller bar mesh' size of the trap net. Gill and trammel nets select most heavily for Gizzard Shad, the catfish species, the bass species and Freshwater Drum. 6 ,
All three types of~ sampling gear select heavily for the crappie species. Physical water quality measurements are taken each sample day in all four areas. Since there is no sampling in December and January, the data for these months is missing. Lake levels are controlled by nature and the Corps of Engineers. 1981 data indicates a variation in lake level of one half foot. Other years exhibit more variation, usually depending on the amount of rainfall. The lowest water levels occur in the summer months and the highest water levels occur in the winter months. Average water temperatures, calculated from 20% and 80% depth data, range from 10 C to 32 C. Operation of Arkansas Nuclear One elevates the Discharge water temperature slightly. In 1981, the temperature ranged from .5 C to 4.5 C higher than the reservoir temperature. The highest temperature differential is observed in the spring and fall. Discharge temperatures are maintained at a lower level in the summer months to . minimize the impact on dissolved oxygen concentrations. Examination of the dissolved oxygen concentration data reveals that only rarely does the Discharge have the lowest dissolved oxygen. In fact, the Channel and Backwater are observed to have the lowest concentrations. The Backwater is also observed to have the highest amount of turbidity and the Intake i the least. i1 7
-Age and growth data for 1981 for various sport and commerical fish species is presented in Figures 8 through 21. Each species is separated into (1) each of the four sample areas, when present, and (2) all age and growth data for the species is combined to estimate the reservoir age and growth trend for the species.
4 The age and growth trend of each species is observed to vary from year to year. In 1981, the Backwater had younger Blue Catfish, four year olds, than it did in 1980, eight year old fish. The Intake, Discharge and Channel all had younger Flathead Catfish in 1981 than 1980, with the 1981 age of one year old compared to two to five years old. No Largemouth Bass or White Bass were caught in the Channel in 1981 and only one (1) one year old Largemouth Bass was caught in the Intake. White Crappie were not caught in the Discharge in 1981 while there were several in 1980. First year fastest growth for Blue Catfish was similar in all four sample areas. Channel Catfish, Flathead Catfish, Freshwater Drum and White Crappie exhibited the fastest first year growth in the Backwater,- Largemouth Bass the fastest in the Discharge and White Bass the fastest in the Intake. I Gizzard and Threadfin Shad are known to be excellent forage fish for a large number of predator fish species. This is true for Gizzard Shad until they reach approximately 5 inches (130 mm). The species grows i 8
rapidly and can become fairly large in size. Potential overcrowding could result if a substantial number of individuals become too large for majorpredation. Introduction of Threadfin Shad is designed to not only provide additional forage but also exert a suppressing influence on
-Gizzard Shad populations through species competition. Reservoir data reveals this to be true. When Threadfin Shad appear in large numbers, the Gizzard Shad population usually decreases. The converse is also true (Figure 22).
The success of the Threadfin Shad population appears to affect the number and condition of predator fish species as well (Figures 23 through - 28). The bass species increase or decrease consistant with the rise and , fall of the Threadfin Shad population. This appears to be generally true for the crappie and catfish species. However, it should be noted that the weights of some of the catfish species actually increased while their number decreased corresponding to the decrease in Threadfin Shad numbers. It appears that Threadfin Shad compete with the catfish, primarily Channel Catfish, and adversely affect the catfish's condition (Figures 27 and 28). Striped Bass appear to be infleenced, probably indirectly, by the Threadfin Shad population success, in this case failure. The observed decrease in White Bass population in 1980 and 1981 may be responsible for the slight increase in Striped Bass number and the significant increase in their weight (Figures 23 and 24). 9
A general declining trend is observed for the crappie species, especially Black Crappie (Figures 25 and 26). White Crappie exhibits several peaks in population. However, each peak is smaller than the previous one and if the trend continues, the population is declining. A possible contributary cause for the decline in the areas sampled may be the sampling efforts of the fishery survey on the crappie species. Use of 1981 gill, trammel and trap net and'rotenone data were used to calculate the impact of the sampling effort on the adult fish in the reservoir. The crappie species are the most heavily impacted (Table 2). Consideration should be given to reducing the sampling effort in the
- fishery survey.
l 5 1 d s 10
e la nLE 1 PEwCENT bu VIVAL ilF SPaasE9 FIbN Sf It11 AL CATC1 LFFDHT r17 dIATI(h FO- tu7a IMWJUsH 1981 NaTE PEwCENTAl,Es 64t A T E r< twAN 100% AWE CAoSED nr A LAhGt9 NPcFu uF F i sit IN IFE 4tJ WATER TPAal IH4N I~ tot *ETEk NFI AvtnAst oldC1AaGE INT 4sE 3ACa*AIE8 C n A i, Ntt F ,3W Tot YEA 5 A4E4 C Akta n AHEA A ArtA D yEAW 1974 1.1 2.a 2.1 3.4 d.3 197d u.o 6.* 9.8 d.n 3.o 1970 140.d kM.9 Idd.4 tid.s tio./ 177/ e43.0 12.5 51.1 12.e Sv.9 117o 13.3 15.0 1.3 m.4 lu.3 [ 1979 3.5 d.o 1.9 c.4 d.* 170u 7 . ti 4.3 3.1 0.7 4.0 1981 134.0 157.9 03.o 1o.3 9d.)
& - 7 w a TadLE 2 FISMENY SURVEY IMPACT DN SELECT NESERvoIR F I Set POPULAlluNS FOM 19e1, OETERMINEU dy TOTAL CATCH EFFnsi FRJs RuldsatE, Twap ngT, inA1"tl NET Anu GILL r.E l PATA 4 CALCULATED PERCENT IePACT uk RESERvulH SPECIES PdPUL A T It t:4 GIZZAR0 SHAD 0.031 THWEA7 FIN Swan 0,031 CHANNEL CATFISti 0 , 0 3 <4 _, uLuE CATFIdH 0,095 N FLAinEAD CATFTSH 0,10H aHITE oAdS 0,oo7 STW1 PED dASS 0,11'1 oLJEGILL SUNFTSM 0,031 nHITE LRA8 PIE 0,39% tiLACA C*APPIE- 1,a29 LARGEMJijfH BASS 0,032 FRESH.ATEw.DRos 0,032 LONGEA4 S U N F i s r* 0,n3n
.. . _ =
ic l i FIGURE:1 i-GENERAL TREND' 0F. FISH POPULATIONS IN DARDANELLE -RESERVOIR-YEARLY ROTENONE NUMBER PER ACRE BY STATION FOR 1974 THROUGH 1981 STAR SYMBOL = BACKWATER AREA A
- TRIANGLE SYMBOL = DISCHARGE AREA C 15000-14000f 13000- ,
120002 11000f _ e N 10000f . U : M 9000-B : 1 E - l R 8000-'
'P : ,
E 7000- - R A G000-C : s R
.E 5000-
. 40002 - 3000 3 2000 1000-~ 4
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1973 1974 1975 1976 1977 1978 1979 1980 1981
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YEAR 13
r IEhERAL TREND OF FISH POPULATIONS IN DARDANELLE RESERVO 1.. ' YEARLY METER NET TOTAL NUMBERS BY STATION FOR 1974 THROUGH 1981 STAR SYMBOL = BACKWATER AREA A- ' i- SOUARE SYMBOL =lNTAKE AREA B DIAMOND SYMBOL = CHANNEL AREA D " TRIANGLE SYMBOL = DISCHARGE AREA C 250000- -
) 2450002 2400002
- 2350002 2300002 2250002 2200002 2150002 2100002 -
2050002 2000002 ' ' 4 1950002 ' 1900002 f I850002 1800002 175000-' , 170000- l 1650002 1600002 i 1550002 1 4 T 1500002 0 1450002 f T 1400002 I
-A 1350002 L 1300002 1250002 N 1200002 U 1150002 ti 1100002 B 1050002
- E 1000002 4 R 950002
. -900002 850002 800002
- 750002 700002 G50002 '
600002 550002 500002 1 450002 ,
> 400002 :
350002 300002 250002 > 20000- , 15000- .
~
o
- 100002
, 5000-] _
E W 0
- 0. . .,- .,.
i97.3 1974 1975 1976 1977 1978 1979 1980 1981 YEAR 14
FIGURE 3' GENERAL TREND 0F FISH POPULATIONS IN DARDANELLE RESERVOIR YEARLY MID WATER TRAWL TOTAL NUMBERS BY STATION FOR 1974 THROUGH 1981 STAR SYMBOL = BACKWATER AREA A SOUARE SYMBOL =lNTAKE AREA B DIAMOND SYMBOL = CHANNEL AREA D TRIANGLE SYMBOL = DISCHARGE AREA C 35000' 34000-- ~ 330002 320002
.310002 30000-4 . =29000; 280002 '270002 260002 250002 -240002 23000-~
T 220002 0 210002 T 20000-A 190002 L 180002 I 170002
.N.i60002 -U i5000-M i40002 8~130002
. - E 12000-R 11000- < '100002 9000-
'80002 , 7000-i 60002 50002 40002 30002 1 20002 0 100 -- - - - _ y 1973 1974 1975 1976 1977 1978 1979 1980 1981 VEAR 15
FIGURE 4 GENERAL TREND OF FISH POPULATIONS IN DARDANELLE RESERVOIR YEARLY SHORELINE SEINE TOTAL NUMBERS BY STATION FOR 1974 THROUGH 1981 4 STAR SYMBOL = BACKWATER AREA A SQUARE SYMBOL =lNTAKE AREA B DIAMOND SYMBOL = CHANNEL AREA D TRIANGLE SYMBOL = DISCHARGE AREA C 27000-260002 250002 240002 23000 - 22000-210002 200002 a 190002 T 180002 0 170002 T 160002 A 150002 L 140002 130002 N 12000- " U 110002 M 100002 8 90002 E 80002 R 70002 60002 ' 50002 40002 30002
~ !. 02 .. ,. .i. ...
1973 1974 1975 1976 1977 1978 1979 1980 1981 YEAR l t 4 4 16
FIGURE 5 GENERAL TREND OF FISII POPULATIONS IN DARDANELLE RESERVOIR , YEARLY TRAP NET TOTAL NUMBERS BY STATION ., FOR 1974 THROUGH 1981 STAR SYMBOL =3ACKWATER AREA A SQUARE SYMBOL =lNTAKE AREA B DIAMOND SYMBOL = CHANNEL AREA D TRIANGLE SYMBOL = DISCHARGE AREA C 1000- i 9752 ! 9502 : 9252 4 9002 r 8752 ' 850-8252 ' 800-i 7752 7502 7252 ' 7002 6752 6502
- T G252 4-0 6002 T 575-A 5502 L 5252 5002 i N 4752 U 4502 -
M 4252 ' B 4002 i E 375i ! R 350- .
, 325f -
300-4 275-~ . 250-
=
2252 2002 175- c ^ , 150-
- 1252 '
1002
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- O'.g .,. g. =4 .,. .g. 6' '6' '4 1973 1974 1975 1976 1977 1978 1979 1980 1981 YEAR 17
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-FIGURE 6 . GENERAL TREND OF FISII POPULATIONS IN DARDANELLE RESERVOIR YEARLY GILL NET TOTAL NUMBERS BY STATION FOR 1974 THROUGH 1981 STAR SYMBOL = BACKWATER AREA A i- SOUARE SYMBOL =lNTAKE AREA B DIAMOND SYMBOL = CHANNEL AREA D IRIANGLE SYMBOL = DISCHARGE AREA C .1800-17005 -
4 1600i . 1500-1400f _ 1300f . 1200f 0 1100 U T : A'10002 L : - i 9002 N : i U 8002 i t1 : B 7002 E : R 6002 500i - 400i - , , + 300i 200 U 100 U , 02 ,,, ,,, ,,. ,,, ,,, ,,, ,,, ,, I
'1973. 1974 1975 1976 1977 1978 1979 1980 1981 YEAR T
1 18
FIGURE-7 GENERAL TREND OF FISII POPULATIONS IN DARDANELLE RESERVOIR <
- YEARLY TRAMMEL NET TOTAL NUMBERS BY STATION FOR 1974 THROUGH 1981
^ STAR SYMBOL = BACKWATER AREA A SOUARE SYMBOL =lNTAKE AREA B DIAMOND SYMBOL = CHANNEL AREA D ; TRIANGLE SYMBOL = DISCHARGE AREA C 1800_
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- R 600f .
500f 400 3002 ' 4 200i . , 1002 - 02 .. i- i. ,- ... ... 1973 1974 1975 1976 1977- 1978 1979 1980 1981 YEAR f 19-
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i FIGURE 9 CALCULATED GRONTII IN INCliES OF SPECIES OF FISII FOR TIIE DARDANELLE RESERVOIR FOR 1981 y SQUARE SYMBOL = AVERAGE CP.0WTli TRIANGLE SYMBOL = SLOWEST GROWTII STAR SYMBOL = FASTEST GROWTIl SPECIES = BLUE CATFISH 2 4 -- 23; 22i . 21i _ 20i _ 19f . 18f . T 17-~ .. 0 - T 162 A : L 15i _ L 142 E : N 132 G : T 122 H - 11-~ l : N 10--~ l 9-N :
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.c=aggf.. ST..R aTMBJLs6 Aalrmf GEC2T!I SPfclF5=0=gggr. re '< t tg 4 4F * = 31 t?g a'?E 24- >
24-23-
- 23-22- 22 21-' 21U 20- 20-89- , o g-16- 13-t 3 7., y g p.
O ' f 16; O t 16-' l A A l_
- L 15-
- L 15-L 14- L to.
C m 13- ( : g 33; 4 0 : 5 f 12 . f 12-' M E il ; n 36
. I I e N 03j , u 102 8 9! I 9- # m C 8. c g' N n f F- E F-9 $
6: _ - 6-' S2 3-4- 4 3- 3-
' 2- ~
2 I I- e. 0- 0-0- I 2 3 4 5 6 7 8 9 13 0 3 4 1 2. 5 6 7 8 9 to
.. .er i ,r.ss - 4cc i,.etes
- -5
[
..s
- 1. -
. ia . ..m. ,. m, e-.
e -N-
FIGURE 11' CALCULATED GROWTil IN INCIIES OF SPECIES OF FISI! FOR THE DARDANELLE RESERVOIR FOR 1981 SQUARE SYMBOL = AVERAGE GROWT11 TRIANGLE SYMBOL = SLOWEST GROWTil STAR SYMBOL = FASTEST GROWTil SPEclESuCHANNEL CATF1SH 24-23-~ 22i _ 21i . 20 ' 19f . 18f . T 172 0 : T 162 A L 15-i / L 142 E : N 132 G : T 12f H - 112 1 : N 10-' I 92 N : C 82 H : E' 72 S : Si-5-
-4i.
3i_ i j. 25_ 1- : 05 'I
.,- ,. ... ,= ,. .,. ..
0- 1 2 3 4 5 6 7 8 9 10 ! AGE IN YEARS 23
~ '~
FIGURE 12 -- CAlftlIATED CR07Til IN int!!r$ Of 1,PECil:S OF FIS!! BY Af1A for.1981 CAtti't.ATED CROTT!I IN INCt!ES Or SPECIES OF F!b!! DY AITA FOR 1931 S4t'4FR bi4PCLeAtttALE GPC* Tit l' TartA%LF SVufs01.ste13 sT 6keeT.I $4't'Af'E 5) ntBOL=An13A6F 61'09f18 6 TAN TRIA%G'E 5)WJ2.*>tdeE=7 hkMTil
$*ttlf t st e t.h ast, tfWL t *4*rr*.
Ahn,La7a EkOWit.t re s.t
. e tre % TAM bWLJLashaI* 3F &kD9*'I 5*f f f f S*
- L 4 'a' 4 3 C 4 F8k!A 94f **igtsef
$4- gg.
83-33 tt- gg..
'20-33 .
30-
- 20-19- gg;
! 98- , pg.
f IF-8 9 gy;
&f.84- 0 t g62 18- f g3 .
L I42 , g g,j E e 13- ,E g3 8 e [ '8' { va; g ' 16-N 9 0-u 3 0-I..-
=
si F-
. :2 .
[ .- p. s-s- 4-32 , 2 3; l-e.
. . . . . . . . , O, # 1 2 3 4 5 6 9 F G s2 0 2 3 e 8 3 6 7 8 9 10 4CE le TE498 tCE Ig Ytatt
? I \ - --. i ! CAIIUI.ATED GROBTI! IN INCIIES OF SPLCIES OF r!S!! PY AREA TOR 1931 1 CA111't.ATED Cr.ONT!! IN INCliE5 0F Sa'ECICS CF F15I! BY AREA FOR lb81
- - 6Ct'Att. bintitSLa 4'.II' ALE GROWTTI SQL'ARE SIMTCL*A\ERAGE LRO1Qt r'
TR't%LE bi400L=$1cmEST ndelli TRIA%LE SnWOL*3LdWt'ST LMelli 5ff*'tS . 51AR* t'nia3bWEOL* ca tf tFAa!EST sg awf 620KT*I 4 -(= ,3 r, geacttg. STAR a ._ nWPOL*FA51T&T e v te3 cg*cisg GROWTH asge.; fr. 4ag 34- 24-2 3 -' 23- i Elf , 8t-ali ti-30- 30-80- 89-BOJ 63-f SFJ t 3 F. 0 0 f 15-'
- t it- '
A 4 L 15- L 35-s 1 14' t
. L t o- ,
i a 13 a g3; 6 C l f 12-- t 3 2-R M !' 81 . et. 1 e 504 I
, a 10-l 9' I 9-e a
- C 4 C 0-i -
n
- I Fa I F-
. $ t 8 l .. .. ,
- s. - . ,.
;4: .. l 3- 3-I l 1- 3 l
- 0. . . . , o. . . . . . .
O l 2 3 _e _5 6 F e 9 50 0 1 1 3 4 '1 8 7 8 9 10 4Cf 59 ff t93 4CC lu f Etel
- i. i
. . . 24 ~ _. - - _ . j t _ s_- _ . , _ -
FIGURE 13 CALCULATED.GROWTil IN INCIIES OF SPECIES OF FISil FOR TiiE DARDANELLE RESERVOIR FOR 1981 SQUARE SYMBOL = AVERAGE GROWTII TRIANGLE SYMBOL = SLOWEST GROWTli STAR SYMBOL = FASTEST GRONTil SPECIES = FLATHEAD CATF1SH _ 2 4 -- 23i _ 222 _ 21 f . 1 20f - 19i . 18f _
!' T 172 O :
T 162 A : L 152 L 14 U E : ! N 13' G : T 122 l H ': 11 2 1 : N 10i . N : C 8-~ H : E 72 S : 6-~ 5-4f . 3i . 02 a- 6 ..- i. - ,- ... . .. . .. . .. ,, ., 0 1 .' 2 3 4 5 6 7 8 9' 10 AGE IN YEARS j 25
~ ~ e+r +,.---tr - ,m,c y T 1 7
- - ~ -- - \ , . . . . .
I FIGURE 14' . - - l 3, CAlfU!ATED LEOTT!! IN INCtlEn OF SPECIES CF i1511 DY AECA FOR 1981 CALCUIATED GROFTII IN int!!Eh O!' SPELIEh 0F IIst! DY AEEA FOR 1983 NGL'Att SY4acLaankRA6F LRO3ill sotturt bWh0L=A%TPA6E G30Tril 181A%LE biilNLaba.p*thi 6kOW115 TFJ*%LE t)MxLssteerst 6hcaT18 47Am a Stak nWBJLaf taTLbf L30tril g*f t lf t.nksJLatantLa.r Dg ,g ett e eubkourI8s se tt 4 5*f r t * * ** m 4-f**,*taaf L, . to - 34-23- 23-i 32- 22-24- ti- ! r to- 20-I st- e t-18- IS-t gr. 89-4 IS-1 16 , .' 4 39- L I S-E to L to-( 1 E l - u 6 3- e 13-
} '
e a f 62- t li-M M II" 8'" y . g u 3 0- p 402
.I 9- t 9-
- h. m -
e
'. C 0- C 8- + se M ?, E F- E r-S :
5 - 6- 6-S- 5-4- 4-3- 32
! 2 2-t- I-4: 0. . . . . . D. . . . . . ] 3 1 2 3 4 5 6 F 4 9 to 0 8 2 3 4 5 6 r 5 9 10 4ct L4 fft93 40f 19 fiets ) -
1 i.
~ **~
p _ CAIIIAATED GECWTil IN INCIIES Or SPECll!S OF FI5it DY AFIA TOR 1981 CAICULATED CROTTil IN INCIIE5 0F SPECIES OF FIdII BY AF.EA FOR 1981 SCUnt SWI DI.=A1TP4GE GROWTil TRIAh!.I stilNLestem esT STwiti SCUAER Sutt:0L=AtIRAGE Gf'08.10
&IAR hikb4LaFAntLar GPo*Til TRIAh114Wh0LaalenE2T 67.0 ant ** E CI F1 <9.at 4 4 E * **
- PtF '. STAR
$Me l f S= SWtiOL*FA>TES.T 04.lg GRoar!!
e9Es g.stwetcr 24- to-23- 33; 32- gg- o 212 33-23- 30
- 89- , g g-is- i s- l t it- e ir-0 0 t 16- ~
4 t 16 - a L 15- E es-t to- 4 is-E t e i3- a s 3-6 s t $ 2- t $3; M M ll- lB-W 60- N 10-
, .: 7 , ,: . m .
a 4 C E- C 4-
} M M
i k
#~- '"
4 s g.
- . # 4- 4; i
3 3- 3
'3- E-i+ i-0 a 3
- s a r e e 30 e a a 3 4 3 e r e. , io
, - . .cr i= eros , .a i .t.u k ,I -
26 w['_
FIGURE ~15-CALCULATED GROWTII IN INCIIES OF SPECIES OF FISII FOR TIIE DARDANELLE RESERVOIR FOR 1981 , SQUARE SYMBOL = AVERAGE GRONTII TRIANGLE SYMBOL = SLOWEST GROWTI! STAR SYMBOL = FASTEST GROWTli SPECIES = DRUM 2 4 -- 23-2 2 -- . 21-~ 20h . 19f . 182 T 172 0 : T 162 A L 15f L 14- ~ E N 132 G ' T 12-H : 112 ~ i N 10; l' 95 N C 8-H : E 72 S - 62 5-~ 4 -- 3-~ 2i _ If
. 4 0-~ !
0- 1 2 3 4 5 6 7 8 9 '10 AGE IN YEARS ; jh 27 -i J
- ._ . _ . . . . - . ._1 ..=.- . __ ._ __ _.
FIGURE 16 CA!41/L4TED 6F.0ET11 IN INL!!LS Ol' SPECIES OF Fidll liY AI:EA FOR 1981 CALCL*taTED ORonT!! IN I,NCILES OF SPECIES OF fl>Il BY AREA FOR 1981 bet' APE SYlf.60Le&\tF49* CR0efft SQUARE 6W90Ls45FRAGE CROW"18 TE14%LE m)'Juotsatcetsi e,f.051H TRIA%LE b)OJ13LG 81 at (,1'OR Ill b7AR bir>>LJAsR*T CRONT11
. geretts. brat AvsoL-f g e *r F* v'* as1Tsf
- n 5 5 t,6*u rre
- gare.gersaa e rg ger g g t s.t a git =3J f g 9451 atf 4*t4f 44E 24- 24-33- 2 3-'
22 . 22-3l- 21- ] 30- 19' I 49 I t- ;
. le- 102
- t 3 F- t 9 7- * *
[ 0 l , o r t 162 af 36.
- 4 L IS- L I S- l L 6 4- L to- [
t t u $ 3- u 3 3- [ 6 C e f 82 ' f3*. as N ll- li- ' g . : 3 s to- a t o- l I l SJ B 9- ' e . N C 0. C 02 e ! en - n + t F- ' _ E F- '
$ 5 6- 6-5- 5-4, 8-3- 3-24 2- ,
la t-F 3, . . . . . 0. . . . , . . I O e 2, 3 4 5 6 7 8 9 to 0 4 2 3 4 5 6 7 8 9 la ., 4CF le ft 441 - act 44 flatt i A _ . _ _ _ _ ,_ I , + I l CAlfL'!ATED LR0Will IN INCL!ES Or $PECIES O'r' FISil DY AREA FOR 1981 ! t
$Qt'ARE SYh0L=AtLR4 E L&ctril TREA%I.E SWBOL=aLJur.b7 6f'C9 fH .I STAR bhBat=FAalthT CRONT14 i l SPEC 1f $as a4Jf MJJ 'M 9 t sS 44f 4 *Di S.*%44Cf f l ! ?
2*' , { 23- ' 22- [ j ti- I r I - 20-
- l L i.-
1> 99- ' i 10-f IFd h IS-i t t iS. - .i f t to-t i L .* a 13- l I g- u 12.- t e [ g a l']
, m io: i.
I-' n I Sk C 8-M t 1- , 6- ! S- d k 4' 3- -- 1 3- *
- l. I-
'( ~, . . . . . . .
O. 1* 3 3 4 5- 6 F e e'.30- r aGF le trats "
, - 28 w.em +.g* -- c -e" -@. *P e *-- %+-"y9' *" -'
l.
~ FIGURE 17' l
l CALCULATED GROWTII IN INCIIES OF SPECIES OF FISli FOR TIIE DARDANELLE RESERVOIR FOR 1981 . l. I SQUARE SYMBOL = AVERAGE GROWTli i TRIANGLE SYMBOL = SLOWEST GROWTII STAR SYMBOL = FASTEST GROWTli SPECIES =LARCEMOUTH BASS i. ! 24- ! 23-1 22i -
~212 20-
! 19i . I82 l T 17 0 : l i T IGJ I A l L.1Si
-L 142 E :
N 132 G - T 122 H - 11-1 : N 10J 1 92 N. : 1 C Bf r H - l E 72 S : 6- - S~ l : l '47 , 3f .
~2i i-1; l- 02 i ,. 3 ... ... .. ,,,,, , }
O 1 2 3 4 5 6 7 '8' 9 10
't AGE IN YEARS ~
29
--w H '
j .. - _ . - . . - - - - - . . , FIGURE 18
] CARUuRD CROOT!! IN WCHE5 OF bPEUES OF FI5H DY REA FOR 1981 CALCLUTED CE0rn! IN INCHES OF SPECIES OF FINI BY Ar.EA FOR 1988 ) SQL'ARE biktasaurat.E LFoWTtt bet! ALE b)1tPOL= auras.E LL'OsrII
,1 Tk1AN612 5)MdCL*al.n#Laf 430Tnd tit 1A.%LE hthcts>LO3Eb7 6kc4DE
] $1AR $WhXal'A%TITT LPC#Til > TAR saf et ts.s,,t ,ve0L=t'As $7Ff t f 5 + =9. ' E *
- i1 4 f 4 9'f *.a rf t rs Sees as;agr Gr.cua.i gr;4reet
- j. ... ..-
J 23- 23- ~. St-' 32-p' 31- 31-20- 23.- i 19- *
$9-10- 182 l . t IF- T $7d 1 0 - 0 : "
j f it- t 162 w A : 4 L IS- L 652 {- t 14U L led / 4 r - L e $ 3- u 13-i 6 - C 4 . f $ 3a f 4 eg ; e, i t-
, lla , y 13- .
a a iO- u 30; f' I 9- l 9-g - m C 8- C 4-M - M E t- T-
- i 5 :
E
) 6- 5-55
- 3-e- 4- '
j 3 3-2- t-si sq
'0' I 2 3 4 5 6 P 8 9 10 0 -2 3 4 5 5 6 F 4
- la ACE 14 ff ett ofE Ig fitt1 f.
e _ _ . . ~ . . . . .
..._..c .- --
t t g CA14ULATED CEOriT!! IN INCIIES OF SPECIES OF FISI! BY AREA F0P.1D81 SCL'APF Snf33L= 6TPAGE GEOCI t TL14.%1 5WNLs5LOWisT 6:241
' l 58ECif STAa5= velSYWBJi=6ASTEst *f f o r tU4 0 : er** L.kOW!?3
- Cf '
24-23-23-I 3' d
- l
' f- 20 192 i.-
e 0 i s L 15-4 i e 'A'
- l '
4 13J l 3 r G : t a 35-8 m 10-
, I 92 i a :
C i es - t. t F1
-6 Gj r .. S- . {.
3; E-la 3-O' B J J e S 6 7 4 9 ,80 4*E 14 'ft4S
. . . 30' 1 1
.+ -- .--
FIGURE 19 CALCULATED GRONTli IN INCIIES OF SPECIES OF FISII FOR.TIIE DARDANELLE RESERVOIR FOR 1981 SQUARE SYMBOL = AVERAGE GROWTH TRIANGLE SYMBOL = SLOWEST GROWTI! STAR SYMBOL = FASTEST GROWTIl SPECIES = WHITE BASS
'24-23i _
222 21-~ I, 205 1 l 19-; 4 ' l 18-t : $ T 17 '
- i. O j T 16-A L 15i .
- - L 142 E
i N 13-G - T 122 H : 112 ' 1 : N 10f I 92 ! N : C 8-~ H : E 72 S : 6i , 5-~ 4f _
'l-0-~
e' i- .- O. 1 2: .3 4 5 6 7 8 9 jo I I AGE IN YEARS .. 31 4
-f 1
i- -
....n.- . . . . .
- y =, * *
! 20 'D 6RONTil IN 1X(til'h 0F SPEC.lES OF FIS!! DY ARE4 FOR 1961 CA14t;tATED GP01tT!I IN IXC!!!!b 0F SPECIEh 0F fibli llY ALEt FOR 4031 t
i
- j. 60UsSI bWD0 lea)TPAf.I G3057:6 640A&E SYMEct.4AnTisA t GROWTil 6 TIJA,hLE b) W'm)LettoWEit e.140479: Tm35%LE Sthplastchst %Kot&al k'- STAP bWLJel'AaTEbf L*.3Wril STAR b)kBJL4ASTT37 LROIT16 9'f ci t* =e s tf ( = =* * : t asf 4 =64f te4 f f t . 1*ffit9ad% 't Me**,f tw o..w'auf 2e- 2s-
*, 23- 23-l' ta- - 22-alj II- \ 20- 20-992 89- . IS- 88-f 174 " ' IFJ
- 0 :
0 : - t 462 f 6 6-
- A :
A L I S- L ll-( lu 8'*i3- / i'*- e 13-E C f 9 2- t s2-91 M 89- , 11-u 10- u 10-t 9- 1 9-e a t 8- C S-es - 4 E F- E FJ 5 SJ 6-5- S-e- 4-3- 3-2- 2-6 e-3 .I 2 3 4 5 6 F e e le '2 & 4 '3 e 1 6 F e e 80 act lg ef tts act le TF491
. . ~ . - . . - - - - - - . -
CALCULATED GRCRTII IN INCIIES OF SPECIES OF l'IS!! HY AREA FOR 1934 50VAft b)MBOL*4EEKALE skOWTil TA14.%LE SYMPetsSLokt&T e MOWT;f SPEclES STAk 5)MbJLet'A>TLb7 wat rr ran**ir ettCAC. NTH e r*sse(L 1 24-
; 23-22-23-19- ,
I S-f 67- , O - t 46-4- L IS-L 14-E e 3 3-6 4 0 42 M ll-1 e 102 a g- a u. C 0-se t FJ S 6-g; . ~ - 4 I~ 3-2 -- l-
.D . , , . , , .
O I '2 .3 4 5 6. F G 9 . le 4CF Ig ft495
. . 32- 1 q
1 L
FIGURE 21 CALCULATED GRONTII'IN INCI!ES OF SPECIES OF FISII POR TIIE DARDANELLE RESERVOIR FOR 1981 SQUARE SYMBOL = AVERAGE GROWTII , TRIANGLE SYMBOL = SLOWEST GROWTII , STAR SYMBOL = FASTEST GROWTil SPECIES = WHITE CRAPPIE 24-2 3 --
.22i .
21 i .
- 20f 19 U 18-~
f 172 0 : T 162 ~ A-L I5i . L 14-~ 13 G :
. T 12 ;
H - 11-1 : N IOi 1 9U N : C. 8f H -
' r. ' 72 S - ~ '6-5~
4 -- 34 . 2i . 15 . Of .- .- ... .. ... , ,. .. I
;0 1 2 3 4 5 6 7 8 9 10 AGE IN-YEARS 33
?
t
. FIGURE 22 PERCENT GIZZARD SHAD COMPARED TO PERCENT TIIREADFIN SHAD IN DARDANELLE RESERVOIR FOR 1973 TIIROUGil 1981 SOUARE SYMBOL =GlZZARD SHAD STAR SYMBOLc:THREADflN SHAD 100-95-90-85-s P 80-E -
i R 75-C - E 70-N - T 65-0 60-F - t 55-T - 0 50-T - A 45-L - 40-
- P -
j l 0 35-p . U 30- f L A 25-T - 1 20-0 - N. 15-j l0-
- - 5 --
1
- 0. g .g. .g. .,. .g. .g. ,.
, .g. .g. .g. .g. 4' '6' '4' '4' '6' 'i' '4' '4 k k ) ! ! ) l ^} } l l- ) } } l \ k l }
9 9 9 9 9 9 9 9 9 9-- 9 9 -9 9 9 9- 9 9 9
- 6. 6 6 6 6 6 6 7 7 7 -7 7 7 7 7- 7 7 8 8 3 4 5 6 7 8 9- 0 1 2 3 4 5 6 7 8 9 0 1 YEAR 34
_ _ _ . . , _ - . .. _ - _~
FIGURE 23 NUMBER PER ACRE OF BASS SPECIES IN DARDANELLE RESERVOIR (THIS INCLUDES SERRANIDAE AND CENTRARCHIDAE SPECIES) FOR 1973 THROUGH 1981 SQUARE SYMBOL =LARGEMOUTH BASS STAR SYMBOL =WHITC BASS TRIANGLE SYMBOL = STRIPED BASS 320-3102 3002 2902 2802 2702 2602 e 2502 2402 2302 N 2202 U 2102 M 2002 8 1902 E 1802 R 1702 1602 P 1502 E 1402 R 1302 1202 A 1102 i C 1002 R 902 i E 802 702 602 502 402 30f -
"% g o ,. .r. .e. . r. t .e. .e. .t. .:. ;
1972 1973 1974 1975 1976 1977 1978 1979 1980 1981 YEAR 35 1
I
;- FIGURE 24 POUNDS PER ACRE OF BASS SPECIES IN DARDANELLE RESERVOIR (THIS INCLUDES SERRANIDAE AND CENTRARCHIDAE SPECIES)
FOR 1973 THROUGH 1981 SOUARE SYMBOL =LARGEMOUTH BASS STAR SYMBOL = WHITE BASS TRIANGLE SYMBOL = STRIPED BASS 4 40-- 392 382
; 37 ~
36- . 352 342 332 322 31-~ 302 292 28-272 P 262 0 25~ U 242 N 23~ j D 222 S 212 202 P 192 E 182 R 17-1 162 A 152 C 142 R 132 E 122 11-~ 102 92 8-~ 72 62~ 5-4- 3-2i
,- =
j 02 a a a
- i. .,. ... .,. ..
i972 1973 1974 1975 1976 1977 1978 1979 1980 1981 l , YEAR k 36
i FIGURE 25 NUMBER PdR ACRE OF CRAPPIE SPECIES IN DARDANELLE RESERVOIR ; I FOR 1973 THROUGH 1981 SQUARE SYMBOL = BLACK CRAPPIE STAR SYMBOL = WHITE CRAPPIE i 320-3102 3002 2902 280f
. 270-L 260~
2502 . 2402
- 2302 N 2202 U 210i t1 200-4 8 1902 E 1802 R 1702 1602 P 1502 E 1402 i R 130J
- 120f i A 110-C 100f R 90-E 802 i 702 ,
602 50J i 402 30f , 4 20- ' h_
'e' 'i' .g. -~c a
1972 1973 1974~ l975 1976 1977 1978 1979 1980- 1981 YEAR b 4 i i t i 37 f
- - . . .JJ-FIGURE 26 POUNDS PER ACRE OF CRAPPIE SPECIES IN DARDANELLE RESERVOIR TOR 1973 THROUGH 1981 SOUARE SYMBOL = BLACK CRAPPIC STAR SYMBOL = WHITE CRAPPIE 40-392 38 7 37 ~
362 352 i 342 332 ! 322 31 2 i 30 292 i 282 272 P 26-' O 25 ' U 24J N 232 D 22-~ S 21 2 202 I P 192 1 E 182 ' 4 R 17 -- 162 A 152 C 14J l R 13: E 122 i 11 2 IOJ
- 9Z 8i 7-62
, 52~ 4-i 2-12 02 -
6- .. . , . ,,, ..
I9I2 1973 1974 1975 1976 1977 1978 1979 1980 1981 YEAR i' 38 2
FIGURE 27 NUMBER PER ACRE OF CATFISII SPECIES IN DARDANELLE RESERVOIR FOR 1973 THROUGH 1981 SQUARE SYMBOL =CHAi4NEL CATFISH STAR SYMBOL = BLUE CATflSH TRIANGLE SYMBOL = FLATHEAD CATriSH 320-3102 3002 2902 2802 2702 2602 2502 2402 2302 N 2202 U 2102 M 2002 8 1902 E 1802
/
R 1702 1602 P 1502 E 1402 R 1302 1202 A 1102 - C 1002 R 902 E 802 702 602 S02 402 302 02 F ~N ^
^
1972 1973 1974 1975 1976 1977 1978 1979 1980 1981 YEAR 39 i
4 FIGURE 28 POUNDS PER ACRE OF CATFISH SPECIES IN DARDANELLE RESERVOIR FOR 1973 THROUGH 1981 SQUARE SYMBOL = CHANNEL CATFISH STAR SYMBOL = BLUE CATTISH TRIANGLE SYMBOL = FLATHEAD CATTISH 40-39-~ 382 372
- 362 352 '
342 332 322 - 1 31 2 j 30 ~
, 292 i
282 272 P 262
-0 252 4 U 242 N 232 D 222 S 21 2
! 202
! P 192 i E 1P2 R 172 162 A 152 C 14-'
i R 132 E 122 11 2 l 9-g: 7: 62 52 4 _' , 3- m %, 1972 1973 1974 1975 1976 1977 1978 1979 1980 1981 - YEAR, l 40
1 l Dardanelle heservior Fiuheries Background Survey Progress Report No. 14 I. INTR 0m CTION A. The report period covered in this document includes January through December 1981. Data collections were temporarily halted at times due to high water, low water, wind, rain, fog, vandalized or lost equipment, and mechanical breakdowns. However, all samplings were ' carried out ao echeduled. Field work during this report period consisted of the following:
- 1. Gill and trammel net combination twice each quarter.
- 2. Semiannual trap netting.
- 3. Weekly meter netting from March 27 through July 31 and semiconthly through October 9, 1981.
- 4. Weekly midwater trawling from June 10 through September 16, 1981.
- 5. Shoreline seining every other week from March 27 through September 12, 1981.
- 6. Annual rotenone samples in area "A" (backwater) and "C" (discharge ) .
- 7. Temperature, dissolved oxygen and secchi disc data.
- 6. Semiannual radiological fish samples collected.
- 9. Semiannual rwi . mgical mussel samples collected from cages.
- 10. Age and growth data, i
f 1 1 41
, _ _,,i, i 4 .E e '?!
4 II. PROCEDUFE A. Site Incation The came five campliru; areaa na previously utilized were used during thic collection period. The arena denoted no refe rence a reaa "A" , "B",
"C", "D", and "E" are depic ted on Figure 1.
B. Gill and Trammel Net Survey A combination of one experimental gill net and one trummel net was set in cample areas "A", "B", "C", and "D" for two days of fiching twice each quarter. Gill neto were 300' total length, comprised of 100' each of bar mesh nicea 1", 1.5" and 2" respec tively. All trammel nets were 300' total length with an outside wall of 14" bar mech. Two cizen of incide wall traccel netc were employed. Inside wall bar meacurements were 1.5" and 2.5". The larger 2.5" trammel was fished the first cumpling period and the cmaller 1.5" trammel was fished the second period of each quarter. Unusually high nu ibers of skipjack herring and striped baan were taken in the August and Govember nettings. High net mortality occurred in both specica, especially okipjack herring. Gill and trammel net data are presented in Tableu 1 through 12. 42
f . I f l C. Trap Net Survey 1 ? Trap netc employed were 5/8" bar mech 16' long, a frame 6' x 3', a i lead 100' long by 3' deep with 5/8" bar mech. Trap netc were cet on May 18 through May 23 and November 10 through November 15, 1981, and fiched for five consecutive days each per.i)d in cample areac "A",
"B" , "C" , and "D" .
A total of 590 adult threadfin chad were removed from the trap not in Area "C" on May 19 At this time the net was coated with threadfin chad egge. These eggs were very sticky and felt granular to the touch. Numerous eggs were also present on the trap net in Area "D" on the came date. Evidently the May 19 netting date coincided with a major spawning period for the threadfin chad. Trap net data are precented in Table 13 j through 17. D. Trawling Survey Two tl Dec of trawls were employed: (1) a meter net with 1/32" delta mech nylon webbing; and (2) a midwater trawl with frame 6' 2" x 2' 6" and 8' of 5/8" bar mech #6 twine, 8' of 3/8" bar king mech, and 8' of 1/8" bar delta mech on the cod end. (1) Meter Net Weekly meter netting began on March 27 through July 31 and continued y 43
[7
?
l b semimonthly through October 9,1981. Sampling Areas were "A",
"B", "C", and "D". Two trawls of approximately five minutes at ~ C 1,000 RPMs were made in each sample area. Fish in the meter net samples under 40 mm in length were usually keyed to family due to the large numbers and e=all size.
Meter net data 'for May 1,1981, are incomplete due to a boat mal-function that required over one week to repair. Meter net data are presented in Tables 18 through 21 and in Figure 2. (2) Midwater Trawl Nighttime midwater trawling began on June 10 and continued on weekly intervals through September 16, 1981. sample areas were-i "A",'"B", "C", and "D". Two-trawls of approximately five minutes each at 1,200 to 1,500 RPMs were made in each sample area.- Fish under 40 mm collected in the midwater trawl were usually keyed to families and no weights taken due to gross errors in weighing fish i this small. Fish above 40 mm were placed in 5 mm groups and weigh- -[ r ed. Midwater trawl data are presented in Tables 22 through 25_ and (. Figure 3 E. Deformities ~! _I
- 1. - Enised areas or growths in fish samples. ~! :- -C 'k-p 44 U
i A. Growtha on neveral ept cies of fich were common in each of the sampling areas. Area "A" still produces more fish with growths than the other areau. The cause or effect of this abnormality is still unknown. Thece data are precented in Tables 20, 24, and 30.
- 2. Curvature of the opine (humpback) in fish camples.
A. Only four fich were collected with curvature of the spine. One in Area "A", two in Area "B", none in Area "C" and one in Area "D". Curvature of the spine is noted when the abnormality can be detected with the unaided eye. Therefore, very small fish with curvature of the spine are not recorded. These data are presented in Tables 20, 24, and 30. F. Shoreline Seine Gear employed was a 1/8" menh, 20' long, 6' deep nylon seine with a full bag. Every other week choreline ceining began on March 27 and continued through September 12, 1981. Each sample Area "A", "B", "C", and "D", was divided into two 80' lengths of shoreline giving two separate but adjoining subsamples in each sampling area. Fich collected in the reine under 1.5" long were usually keyed to family and no wetchts taken. Unucually large numberc of threadfin shad were taken in the July ueine camples. Shoreline ceine data are 45
t . y-T preacnted in Tables 26 through 31 and Figure 4. G. Rotenone Samplec C f In cooperation with the Arkansac Game and Fish Commission two stan-dani rotenone camplea were taken in September 1981.
- 1. Area "A" rotenone comple September 8 and 9,1981. ,
- a. Iocation: A cove located across the river and slightly down-stream from the mouth of Piney Creek. t i
- b. Collection cite: 4.1 acres with average depth of 6.O' .
- c. Collection method: 6E pounds of 7% powdered rotenone.
i
- d. Water temperature: 80 degrees F.
l.
- e. Visibility: 16" L
- f. Cover: Brush, marginal vegetation and zuck. l;:
i
- g. Remarks: This cample area was located directly across the c main river channel and slightly downstream from the mouth of f I
Big Piney creek on Dardanelle Reservoir. The mouth of the cove opened directly downstream into the main river channel. 5 t Part of the area conciated of steep, rocky banks; while the fl ll remaining banks were gently sloping and covered with rocks :
+ \1 and timber. This wuc an open cove; with the bottom consisting ;, ]j of clay type colla, rocka, and gravel. Cover conciated of rj ll brush, marginal vegetation and rock. The area was curveyed to r I, :
determine the exac t nize, ' which was 4.1 acres. The maximum ,. 46
l a depth was 16', with an average depth of 6.0' . A block-off net wuu utilized to completely seal off the cample area. A two ( day pick-up of fich was employed in conductind this cample. i The block-off net that was uced to close the area was put out in the dark, and rutenone was diotributed in the water at day-light. This area was cumpled in 1970 and from 1973 through 1981, an a reference area in the !mrdanelle Recervoir Fish l Su rvey . The fish collected in thic nample were worked up in f 2" cize groups. This was done no data available would be similar for any future comparisono of fich species diversity within this particular area, or other related areas of the res e rvoi r.
- 2. Area "C" rotenone cample September 10 and 11, 1981.
- a. Location: A cove located in the effluent bay at Arkansaa l Nuclear One and located approximately 1/2 mile southwest of f f
the power plc.nt on the couth side of the bay.
- b. Collection Site: 6.75 acres with an average depth of 4.2' . .
a
- c. Collection Method: 72 pounds of 77, powdered rotenone. ,
- d. Water Temperature: 91 degrees F. g J
- c. Vicibility: 24"
- f. Cover: Fallen and dead timber, inundated buck bruch, and a few rock.
o I I 1 b iku . 47
{. . . . i
- p t
I
- g. Remarks: This cumple area was a wide-mouth, wooded cove locat-
_f ed in the effluent bay at Arkansas Nuclear One. The banks were { gently sloping around the sample area, with clay eroded banks , caused by wave action at the mouth of the cove. The bottom soils consisted of clay, gravel, mud, and debris. Cover consisted of fallen and dead timber, inundated back brush, and a few rocks. ,' The area was surveyed to detemine the exact size, which was ' 6.75 acres. The maximum depth was 12', and the average depth of the area was 4.2'. A block-off net 600' long was utilized to ' completely seal off the sample area. A two day pick-up of fish l was e= ployed in conducting this sample. The block-off net used - to close off the area was put out in the dark, and rotenone was I i distributed in the water at daylight. This area had been sampled annually since 1971, in connection with the Daninnelle Reservoir Fish Survey. The fish collected in this sample were worked up
~
in 2" size groups. This was done so data available would be similar for future comparisons of fish species diversity within [ this particular area, or other related areas of the reservoir. I Hotenone data are presented in Tables 32 through 33 and Figures , 5 and 6. i
,a 5
H. Environmental Information ' s i Lake levels, weather and lake conditions, dissolved oxygen, water tem-48
~ .. .. . .. .. . . . ..
/? . perature and secchi disk data were taken during fish sampling operations throughout the study period. Sample Areas were "A", "B", "C", and "D". Themal and diccolved oxygen data were collected at 20% and 80% total depths'by means of a YS1 54RC oxygen meter and YSI probe. Tables 34 and 35 presents the above date. I. Radiological Samples l (1) Fish Samples Two semiannual fish camples were collected and cent to AP&L in I 1 May and November 1981. The cample consisted of 10 pounds each ; of predators, suckers and plankton feeders for each sample' Area "A", "B", "C", "D", and "E". (2) Two semiannual mussel samples were collected and sent to AP&L in April'and October 1981. Mussel samples were collected in Areas "A", "B", "C", and "D". The mussels collected from local streams are held in cages 2' x 4 ' x 4' with a solid bottom, 6" sides and ; covered with 16 gauge galvanized vinyl dipped wire. Each cage had . a 6" layer of- gravel in the bottom. Each cample Area "A", "B'.', "C", . ' and "D" contains two cages. - J. Age and Growth Age and growth . calculations were made on ~ seven species of fish collected.- The species'are: White Bass, Morone chrysops; Largemouth Bass, i J 49
._ g 1
ic s Micropterus salmoidea; Whi te Crappie, Pomoxia annularic; Freshwater Drum, Aplodinotus grunniens; Flathead Catfish, Pylodictic olivaris; Channel C Catfish, Ictaluruc punctatua, and Blue Catfish, Ictalurus furcatus. Detemination c the age and rate of growth of a particular fish is accomplished by examination of a scale (or bony ray of catfish) under cmgnification, and interpretation of the markings which typically occur. Breaks in the nomal pattern of growth occur during the winter period of growth cessation, foming " annuli", and ty counting these annuli the age of the fish can be determined. False annuli appeared on the scales of many fish but coald usually be identified by their position or by the , relative degree of crowding of the circular ridges (circuli). The scales , of each fish were cleaned by rubbing them between thumb and forefinger and mounted on glass slidea with Scotch Brar.d " Magic Transparent Tape", . No.810 as deceribed by Smith (1974) Prog. Fish Cult 36(4): 195. All [ t opines were cectioned using a small power saw on a stationary platfom. ' t' This unit conciated of a fixed blade which could be elevated,a mechanical l table that regulated the thickness of the sections, and a sliding table ! to which a V-block and clamp were attached to hold the spinea immovable. All opinec were mounted on glass microscope slides with Duro Super Glue. } Growth was calculated by direct proportion with an aucumed intercept of ' I cero for all cpecies. Finh collected from October 1 through March 31 s 50
0
'1 l
are considered to hnvc an annulus. Data on age and grmith are presented in Tables '6
; thr ointh 4P nrid !#idures thr ough 31. J Figures 16,18, 24, and 28 were constructed from data consisting of only one fish each. As a result the symbols for fastest, average and slowest growth overprinted each other. It may appear that some species, partic-ularly White Crappie, have undergone a reduction in growth during this sample period. However, a different sample size and age structure would probably account for this.
K. Quality Control
- a. Quality control measures were followed during the report period.
Checks and calibrations were made on the following items: barometer oxygen meter flow meters 9
.h weight scales '
t shoreline seine areas gill nets trammel neto meter net i, trap nets bag seine Data for these measures are recorded in the lake log. 51
- r. - -
l L. Maintainence
- a. Boat, gear, and cove marker maintainence was performed as needed.
t Dates and maintainence are recorded in the lake log. M. Miscellaneous
- a. Considerable time was devoted to transferring raw data to computer key punch forma.
t b8 52 .
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i r TABLE 1 TUTAL NJM5E4 UF FISM CAUI.tf DER SI4fl0N Bf UATE AND FU4 TrtE YEad FOR 1 GILL %T 1981 TABLE DF DATE of STATION
._ _ _ .._. . _ .. _ _ . ._. __ _____ 04Tp -
3 TAT 13N .. _ _ ,_ ,,.__ .___ _,__ .____ ,_ F<twJENCYI ped:ENI.IC*ANNEL 64EF 3 lita:<aa la 4EF ATIEF E lIN4 T A<itE wEF d 10!sCM C i A WG) . TOTat_ , _ _ _, __ _ _,_, _ _ _ _ _1 ,,_, , __ _ _,_ , _ _. .. _ _ _ _ _ . _ . . _ . .. _ . _ _ ._ 910d21 1 4? I ei S4 6 33 1. 138 ________,__ _,, . _ , . _ , , _ _ ._ _, __ i 1,56 4 0.33 8 d.00 1 1.2d i . 5.12
.........+........+........ ........,........, . . _ _ _ . _ _ _ _ _ _ _ . - _ _. _ _ . __ __.. _ _ _.. . . _ . _e_910d22 1 0 I oI 63 1 0 l . _. 63 ___Z.________._ [ _ _,
t 0.04 1 0.00 1 d 34 8 0.00 l 2.34
.........,........+........,........,........, . _ _ .. _ _ _ _ __ _ _ .. stud?w I 75 8 to 1 0 4 60 1_ 1 45 ____.__ . ___ . __ __ ,_
2.7M i I 0.31 1 0.00 8 2.?3 I b.3s _ _ ..___. 810313 1 4 i 11 21 1 23 1 93 '~ ~ ~ ~ ~~ ' 0.04 i
~ ~ ~-
1 1.7M i U.19 1 0.*65 1 3.45 u, 416314 8 20 1 31 20 8 17 1 00 _ __ _ _._ ,_____,_ _ _ _. _ _. _. _ 4e I o,pu 1 n,lg 1 0./4 1 0.h3 1 2.d3
.........,........+........,........,........,
__. .. ._ . __ _ -_ _.__ __ _. _ _ _ 810514 I so I ?! I 21 1 47 1 157 _ __, ____ _ 4.45 1 i 0.7e 1 0.oS I 1.74 1 5.o3 _ __2 . _ .. _ .-_ . . _ 810520 1 47 1 61 19 I 30 1 101 _ _ _ _ __, . ._ . __. . _ . _ . I 1.74 1 0.22 I u.67 1 1.11 4 3.15
^^ .........,........+........,................., _. - --~ ~ ' ~ ~~~- . _ _ _ _ _ . . ..810b11 1 4 't i 14 & 59 l 13 l_ 132____.______.._____._._..___.. _
l 1.71 1 0.52 8 d.19 1 0.41 1 4.v0
.........,........,........,..=.....+........,
H10012 1 51 1 51 2i I a 1. o9 __... . __ _,_ . . , __ . _ . __ _ l 1.84 1 0.14 1 0.93 1 0.30 l 3.30
.........,........,........,........+........, _ _ _
TJTAL 34s ,_ 763 180_._ 2095 __ ._.__ , _ . _ ... 29.09 758 . . _ _ _ 12.91 29.u5 . _ _ . .28.44 100.90 (c3NTINUE31 e -
-.ew- - - +-um.<=.-e+---e e-== --- e e, .. .. . .,...-w_--e.-_ .__._._.e-. - em.we, e . __.- --.-.- .._e_,-i.+a-mi m.. _
ea _aw,.g,im. _p ee- e e,*.ese 4e_- _ ..__ _ _ _ wem.amme.-A = %,-aw.ee ., ei. engue <mi e.y._.,_c. ...g's .e.sw4.- *rN"***46 ""ou'48" '8 Wu"*"* * ' " *- *-M*8**#' ' ' ' " . " " * * * * * 'r***'8""#41**m'40 *****48'em** * * = - 'hh* *" "*NW *"***=8*-- m _m e..w emmuu a = m e a6**- e um e- us .+ ~e _e.-coe. emguimsp.summ4 >e.e... - e ame meene . -e.ee+"-ew 4e Whaie=+ -e-e,.i.w **__e-e.- m.es* +-@+_*v 4.-s .4he _ a& - w _. e _ , ,,,, D'.te+.m . am - W . Daume==.-ia.a =em Ow g.-e mu+ g. ..e. eq .e 'waiw. us. e, . equ- ..- he - en me-. u _ . ._ , , , , _
-e +
- mb W e.,__+<., _ s q waw- A- 2 -C%-' M 'M' - - - - - - - - - - - - - - - - - - - - --- -- -
TABLE 1 70 Tat Nu"8ER vF FISH C4J317 PE4 Staf!)N By DATE aaD Fod inE YEAR FDa 2 GILOE1 1981
' - ~~'~ ' ~ ~ ~ - ~ ' TABLE f1F Da1E SY ST4 TID %~ - - ~
DaTE STATDN
~
FwEUJENCY4 pea:ENT IC*A%4gL IBack.ATEi!siadE EIDISCMp 01 _ 14EF D 14 GFF a IEF o IE WEF C I TJfaL
........., .......+........+........+........, . __ .__ . __ . _.. _ _ _. _ _ __-_ __ _810812 1 72 i 53 1 78 1 8 I __ _ 2 1 1 _ _ __ _ . _ .. _ . _ _ _ . ._ _ _ _ _._ . __
l 2.67 I l.WF 1 d.69 I 0.30 1 7.03
.........,........+........+........+........+
_, ____ _ _... 910bl3 .I_ 51' 1 3e i 50 1 11 1,__. 157 _ _ _ __ i 2.15 1 1.41 1 1.s6 8 0.41 8 5.03
.........+........+........+........+........+
_ _ _ _ _ . __ _ . . _ __ _ . _ . _ _ ___ _ . _ _ _ . . _ _810u29 8 28 1 47 I 74 3 57 I 202
. 7.50 .._ ._.. ___ _
i 0.m9 i 1.7u I d.75 1 2.12 i
.........,........+........+........+........+
__. ..___ ._... _ _____.__ _ 810o30 : 46 l 19 I of i 31 I to9 ,_ ____ _ _ _ __ _ i 1.11 8 0.71 I d.49 8 1.37 i b d7
.........,........+........+........+........+
_____.. __ ._ ___ ________ _ . . _. .__ B 114 31 1 75 8 30 i 61 1 165 I .. 383. _ _ . . . _ _ _ . _ _ . _ _ _ _ _ . _ . _ _ . _._ ._ u-u,r i d.7B i 1."5 1 2.34 i ".12 l 12.I3
.........+........+........+........+........+
_ .._ _ . _ . _ . .. _._ ___ 811101 1 35 1- 12 1 76 I 133 i-. 2 5 6 ____ __ _ _ ___._ __ _ _ _ l 1.30 l n.05 6 d 42 1 4.94 8 9.30
.........+........,........+........+........+
___ . _. . __.__.__ _ ._ _. . _. _ . . ___ ._ 611119 1 34 1 40 1 27 1 77 1 dv6 .__ . __ _ __ ___ _ _ _ . .__.__ _ _ _ _ _ l 1.29 a 1.us i 4.12 1 2.8e 1 7.72
.........,........+........+........+........, , _ _ _ . _ _ _ _ _ . . .. ____. __. _ _ .__ __.___ _. 911115 .l.. 43 I 3U i 35 I 03 1 _. . 1 7 1. . .____ .____ __._____. __ __ _ .._.__
i 1.60 8 1.11 8 1.30 1 2.34 1 6.35
.........,........+........+........+........, ,
_ _ _ . _ _ _.._ .___.. _._- ____ . - ._._ ___ T .3 T
- L . _ . ._ 7s4 . 345 _ 7d3.._. 160 2 D 5 ___.__. _ __ _ _._ ._._ ._ ____ __.. _ _ , .._ . .
29.00 12.91 29.05 28.94 100.00
- _sm --
em._.= - , I
, . _ M #6 - . 4.h- .e. * ._ - m h. w .*-e =. ,.,,
W _M eew-epe_-.ea me u.-e e. _ s 2. _ . _a,_..gme,r-a ,d<ee _- %__., . . ,,.e ;p.i., y _- w . .- ' m.* * *- +- prg em& N . k- - .
- _ -g- ...De.eW .4 "' " 4*****"'**49 ****4.**N+ "* *** **" ' " " ' * * ' ' '"" * ^ *'* *' ** . - * *+- k'-_ wh i _ _ - - _ _ _ _ _ _ ___. ____
TABLE 2 TOTAL nEI'JHT UF FISM Ca0Gmf pgw SlailuN dy DATE AN4 FOR TnE YEAN F04
~
3 GILLNET 1961 TABLE OF DAIE Bf STATION _ _ . - ._ . _ ___ _ . .. .. _ . _ .._ ___._ _ 04Tt STAT 139 . .. . _ _ _ _ _ _ _ - - - _._ _ _._ ___. _
. F<EWUENCYI . . - -
PEHCENT ICHANN[L fpACW.ATElINIAkE HlDISDNANFel
~~ -
IMF D 14 WE F A lEF d IE HEF C I TJTAL _ _ .._. __.._ . _._ . ___. _ ._ ll10d21 1 2h I 4 i 19 I 33 I. OS____._____..___ .. _ _ ._. ._ i 2.02 4 0.31 1 1.42 8 2.41 1 6.15
.........,........,........+................., ~
__._ _ . _ . . __ _ _ . _ _ 810422 1 01 01 11 l 0 I . II. __ _. . , . . , . _ _., _ 1 0.00 1 0.no I u.ou i 0.00 1 0.04
.........,........+........+ . ..... ........,
_ _ _ _ . - __ _ ____ ._ -._ ._ -_. __ 810d24 1 52 1 10 1 0 0 63 l 16 . _ . _ . .___ _ . _ _ , _ _ _ _...___ _ .__. . 1 3.d1 I 0,70 l u.00 $ 4.55 l 9.Wh
.........,.................,........+........,
__. . . _ _ _ _ _ ____ 810313 1 2h I oI 9 I to i 53 _ _ _ _ _ _ _ , _ ,_ __ ,_ . _ 1 1.89 i 0.01 0.s4 i 1.33 # 3.09 810414 1 11 1 21 12 1 11 4 3a ._ _ _, ___ _.. ,__._ _. __ ___ u, u.bu 8 cn I 0.12 1 0.nd 1 0.M2 1 2.62
..................,........,........,........, ' ~ -- 810319 I il I li I .
15 1 07 - .. . . ._ _ . 1 0.n1 1.01 1 1.11 1 45a1 __6.32 3.31
.........,........+........t........,........, ._ _ . . _ _ _. . . __ _ --.... 630520 4 9 I 41 4 I to 1._ 36._ _ _ ___
l 0.be 6 0.33 8 d.32 8 1.30 1 .2.01
~ .........,.................t................., _ _ , ~ 410011 22 1 41 22 I 04___.
1.59 1 l 0.23 i 1.59 1 le 1.16 41 _ 4.02 '
.........,........ ........+........,........,
810012 I g9 1 i 7 1_ 12 1. 3 9 _,_ ___ l .1.u0 1 _ 0.04 I . u.54 1 0.n4 1 2,07
.........+........+. ......t........+........,
TJTAL 314 151 355 . 55e _ . 13T5_ _. _... .._. 22.b4 11.01 25.65 co.33 100.00 (gJNTINut3)
..e._. ,_ . .. --.4- -.e...+_m+_=..-wes. -.__e-.- .....,-....-w.-== - * - ==+=.~.e.--.=%.-- . . , , . . . . _ - = - . - - ., -%. . _. = __.
6
.. . . ..--. ---.-.--e- , . .v--. g. - e- e am.- - --
es.* - - p.
-- ---- -.__ -e= .--.-....__ - .- %g e .p ape.%.h h.- ie.e w ese-etee - .-._ =We- ***4.m. . mew-,-. .=_44_. ._'..ye e. e,._.,_e .._% , , . _ _ , , , , , . , , , ,, gg _..
n . --m-w - e.e-e..--ae+ + e -m. -
- -- Y'$
TABLE 2 TO12L aElyMT LF FISn OAu28T ped STAllvN SY 041E AND Fud THE YEAN FG4 s GILLNET 1981 Daft STAT 13N FMLGaENCtl Pl a. C E N T icd 4NNEL ISA"<dATElINTAME diptsCnANGl _ - - - . -
......... ........ ........+.................,
E10512 1 31 I to 1 32 i 10 t 69 _. _ _ _ ., s 2.29 I 1.16 4 2.30 1 0.74 1 ._6.46
.........,........+.................+........+
810b13 1 12 I lu I d2 l Ib Q o2 _ _ _ _ _ __ _ ___ 1 0.95 1 0.74 i 1.o1 1 1.32 1 4.53
.........,........,........+..................
610529 I 5 I $ i de i 32 6 73 '- ~~ ~ ~ ~ ~ ~ ~ '~~~~ ~ ~~ ~ ~ 0 0.36 1 6.60 l d.04 1 2.30 1 5.30 810o30 1 11 1 14 4 36 1 31 I v3.___ ,., _ _ _ i 0.04 1 1.Du i d.62 i 2.2o 0 6.78 m _ . _._ . _.. .._ . _____ _ ._..._ _. 611y31 1 39 8 2$ i 32 6 77 6 114 ..__. . _ _ , __________ _ _ , , . __ _._ ___
-a i 2.nu i 1.42 1 d.30 0 5.63 l 1d.09 .........,..........................+........, ,
__ . ___._ _. . ._.__ ____._ _ _ _ .811101 1 15 i 10 1 34 4 75 8. 13e _ _., _. ... ,_ _ _ ._ .,____ ._ i 1.09 I 0.73 8 d.49 I 5.47 s 9.t7
.........,.................,........+........,
__. ___. . ,. . _.___.. __ 811114 i l ie i 14 i *3 8 50 l 144 -_ _ .. .. .. __. _ _ . . 1 0.75 i 1.02 1 3.16 I w.07 8 9.90
.........,........+........,........e........+ ~ . _ _ . , _ _ . _ _ _ _ . _ . . _ _ _ _811415 . I_ 12 1 12 1 27 1 3o 1. d9._...__._, _ _ . _ L_ _ _ .._ __ _._
i 0.sh I o.91 1 1.9s i 2.7o I a.ws
.........,................. ........+........, ,
_ _ _ _ ___ . _ _ _ _ ___ .__ _ _ _ . _ _ . . _T3TAL ._. 314 . 151 355 554 1 3 7 5 .. . .._ -_ . . _ _ .e _ _ _ _ . . _ _ .. _ _ . _ _ _ _ . _ ._ _. _ 22.84 11.01 _ 23.55 40.31 100.00
.=
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am
.mmim use.- y _ h *e_--e>gema.m..eepee.se gi.m eo em,h w emeyqs .. e,,ee.e e p am , e.,,,,. g-e 6 - . m.p.- - yw=e - p ..eem h..y.W.mme..e.wie.m.um-mm*mWNe w..e.gu.- p *- me ae . , ,me.g. weme m'*-Wew'
- m.w-_ _ege aae+- _.-e.q.h.w-+e ew -
+= ., - i., - -.m e . - -e w-u'- w -w, N-4 ++ +>-e. -Alb+ ----- -
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NUMBER OF SPECIES BY SI&TIuN Fod GILLNET 1981 1 TABLE OF S P E C I E S o. f. . S T a l T ON.-.-.._. _ _ . . _ - . . . SPECIES STAT 109
. _ _ . . - - - . . _ . - - . ~ - - - - - -
P E d C E'. I ICa&%NEL luAC*a&IEl!NTant alarsCnapsi 14EF 3 IW WEF A IEF d IE NEF C 1 TOTAL _ . _ _ . . .................,..........................+........, _, _, _ _ Lu%GNJSL God 1 31 01 0 1 3 6 t 0.11 1 0.00 1 0.00 1 0.11 1 0.22
.................s........+... ....,........,........,
SaawiNUsE GAR I 31 01 28 28 7 1 0.11 1 0.00 1 0.07 1 0.07 I 0 26 _._ ._. .- .................,........+....... ,................., G172Ad3 S4AD i 139 4 54 1 165 3 52 1 430 l 5.16 1 2.00 1 6.65 1 1.93 1 15.9th _
.................,........s........,................., _ _ _ _ _ _ _ __
SnipJ4C$ nE= DING i 100 8 17 8 59 I 299 I 475
~
3.71 1 0.e3 1
.................,........+............. 10 ............, ~
l 2 1 11.09 l 17.63 T n4E10F I N Snau i 5 1 28 21 1 l 10 1 0.10 1 0.07 1 0.07 I n,ng 1 0.37 on = ..===...*....*.,=......=,.*.**..**........+==..=..., __ _ _ _ _ _ . _ _ , 00 GOLDEVE I 11 0 1 0 I o1 1 I o.04 I d.00 1 0.00 1 0 no 1 0.04 _ _ _ . .................,........,........+........,........, Ca3P l 11 l 11 13 3 6 8 31 i U.41 1 0.04 I o.4H I n.22 1 1.15
..........................+........,........ ........,
alvg4 CA4aSUCAC. I 10 1 30 I $1 1 109 1 203 1 0.37 8 1.11 1 2.00 1 4.44 I 7.53 314LL10dT1 udFF4 s 01 11 11 4 6 6 s 1 0.00 i D.04 1 0.04 1 0.15 1 0.22 ~. ~~- -- --.. -- - -* - 01
, HLAC< HuFFALD l 11 I I oi 2 . _ . . _ _ _ - _ . . ._. . ~.
I U.un 1 0.0a I o.o* I 0.00 1 0.u7..-- - - - - . _ - - -
.................,........+........+........,........+ -
alvEd HE3*hSL I oe 1 I 01 01 1 1 0.00 i D.04 1 0.00 1 0.00 1 0.04_ ___._____ _ ._ __ . _ _ .
............................................+........, . - GOLDEN aEonoasE I 11 0 I .O I 08 1 0.00 1 ~~ ~~ ~
1 0.00 1
...................................t.................,
0.00 1 0.00 l _ 0.04 _ CateagL CaTrIsd i 101 1 29 8 29 I 45 1 206 1 3.82 I lede i 1.09 1 1.67 1 7.04 - - - - - - - - - - - - - - - - - - --
~~
T U T al, 7ue 343 7o3 780 2b95 29,09, .- 12.91 .. 29.05._. 24.94 100.w0
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T/ ELE 3 N N L4 0F hPECIES dY S T A T ! um. F0a GILL *,ET 1991 2
\
__ __ _ _ _ TahLE OF SPECIES dY STATION I j $8ECIES Staflh
- p..._____. . . _ . . __ __ . _ _ _ . _ - - _ _ . - - - -
DE4CENI s*.As*EL ina Caa&TElisTAdE platsCaAvst
'8 IEEF 3 IW dEF a IEF is lE dEF C i TOTAL _ _ _ _
dLUE CAIFISm i 134 1 27 I 40 4 47 1 299 1.05 4 1.e2 1 3.25 1 i
.................,'........,........,................., 1 1. u 9 , _ _ __ __ _ ._ ".97 l _ _ _ . _ . . . _ . _ .
T FLafatAJ C A TF IS1 1 11 11 11 1 4 4 0.04 1 0.04 1 0.ca 1 0.04 1 0.15 _-- - - - - - - - - - - - - --- ~ - - -
.w!IE HASS I 13 1 12 I 75 I a3 1 141 l 0 ua 1 0.35 1 2.71 I t.e0 1 5.23 . _ _ _ _ _ _ _ . _ . . _ _ _ _ _ _ _ _. .................+................ s........,........,
STEIPED d433 I 16 8 17 I 64 4 45 i 166
' ' ' ~ ~ ~ ^ ** ' ' ~
1 .0.59 1 0.h5 4 3.27 I t.*7 1 6.16 _ _. .
.auw3sTe 1 21 21 0 1 01 4 i 0.07 1 0.01 1 0.00 4 9.no 1 0.15 _ _ . _ _ _ _ _
cn ...................................+................., G4EEN buNFIb4 1 0 I e 1 0 I oI 6 1 0.00 0 0.22 I c,00 1 0.00 I 0 . 2 2 __ _ _ _ _ _ _ _ _ _ _ _ _ . _ _ . _ _ . BLUE 31LL I 5s 2 l 12 i S I 27 i 0.19 1 0.07 1 0.uS I 0.10 s 1 00 _ _ _ . _ . .
.................,.................+........+........,
Los;E4* SuNF13* I 31 21 2 i 1 I h
. . _ . . - _ . _ ~. . _ _ ._
I 0.11 1 ,,,,,,,, 0.01 1 0.07 1 0.04 e 0.30 _ _ _ ..__. ____ . _ . LAQGE*0JT* eA33 1 0 1 3e 11 18 5 l 0.00 1 0.11 8 0.U4 1 0.04 l _ 0 19 __.__ _ _ _ . _ . . . _ _ _ _ _ ... aa!TE C1&WIE I 56 1 52 1 1%9 : 52 1 309 _
.I 2.04 s 1.93 1 5.51 1 1.93 I .1 1 4 7 .___ . _ _ _ . _ _ _ _ .
BLaC4 C?APPIE I O I 11 0 I , 5I 6 4 0.on 1 0.04 0 0.00 1 3.19 l__._0.22 _ ___ _ . _ _ _ _ _ _ _ i , __ _. __ __ 540G Eit i 4 8 0 8 6 1 51 15 - _ _ ,_. ._ w . . . _.l. .U.15 I. 0.00 1 0.22 I. 0.19 l_.0.36 _ __
...... ..........,........,........,........+........,
F4ESMaalER DRU* ' 1 174 4 65 1 5h i 11 1 326 I b.46 I 3.15 1_ 2.05 1 0.41 1 _12 10 _ ___ _ _ _ _ _ . _ TOTAL 7eu 345 7d3 780 2095 __ _ __ _ . . . _ _ _ _ _ _ _ 2 9 . 0 9 . _. ,12.91 24.05 __.28,9s_ 100.00
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