ML19210B022
| ML19210B022 | |
| Person / Time | |
|---|---|
| Site: | Three Mile Island  |
| Issue date: | 02/28/1977 |
| From: | Nardacci G ICHTHYOLOGICAL ASSOCIATES, INC. |
| To: | |
| Shared Package | |
| ML19210B015 | List: |
| References | |
| NUDOCS 7911010754 | |
| Download: ML19210B022 (243) | |
Text
AN ECOLOGICAL STUDY Of THE SdC #NNA RIVER 1; THE Vi;iNiTY OF THE THREE W ISLAND NUCLEAR STATION Annual Reptert For is76 by George A. Nardacci, Project IMer, and Anociates Ichthyologic21 Associstes,Inc.
P.O. Box 223 Etters, Pennsylvania 17319
~
for METROPOLITAN EDISON COMPANY oo L a ICHTIIYOLOGICAL ASSOCIATES,INC.
Edward C. Raney, Ph.D., Director 301 Forest Drive,Ithaca, New York 14350 February 197 1565 038 7011010 7 h 4
AN ECOLOGICAL STUDY 0F T!E SUSQUEllANNA RIVER Ifl TIE vrC..trY OF TIE TIE 1EE MII.E ISL\SD NUCLEAR STATION Annual Report For 1976 a
by Georre A. ?*ardacci, Project Leader, and Associates
'~
Ichthyological Associates, Inc.
. P. O. Box 223 Etters, Pennsylvania 17319 J !
for SETROPOLITAN EDIS0N C0}!PANY ICICIIY0 LOGICAL ASSCCD.TES, INC.
Edward C. Raney, Ph.D., President 301 Forest Drive, Ithaca, New York 14850 February 1977 1565 039
TALLL OF M .T'.:.U Sec t ion Page OO 1.0 1:tinoDUCTim; . . . . . .. . O , . O. $I O h( N /. . . I 1.t 1.1.1 sewRv.
Fish.
g
- g. .
M lg,
. . 9 9 .9 s ht a.
3 2
2 1.1.2 Mac tr inver teb rat es . .. ... . . . . .. . . .. . .. 3 1.1.3 Anblent '.later Qualtiy . . .... . . . .... .. . . . .. t 1.1.3.1 Physicoctienical Parameters . .. . . .... . . .. ...... 4 1.1.3.2 Fatal roliforn . . .. .... . . .... . ..... . . 4 1.1.4 Thernal Plume . Napping . . . . . . . . ... . ... . . . L 1.1.5 Cf fects .'f coolin; Ix.er (alt t rif t en Agricultural crops and *:atural 'legetatten. 5 1.1.E.1 Pla r.t Fathogens. . ..... ... . ...... .. 5 1.1.5.2 Quartitative vegetatic:' itud tes. . .. ....... .. . . . . 5
~
2.0 F IS!!
Robert W. "alick, Jr.
2.1 Methods. . . . . . . . .. . . . .. . ..... ... . . . 6 2.2 Results. .. . .... . . ......... . . . 9 2.2.1 Trapnet ... . . . . ........ .............. . 9 2.2.2 Seine . . . . . . .. .. . ... . . . ... . . ......... 11 2.2.3 Reproductive Status And Ccndition Factor. . . .. .... . . . .. 13 2.2.4 Parasites . . . . . .. . . . ......... ..... ..... 14 2.3 Discussion . . . . . ... . ...... . f* . . . ....... 15 3.0 MACR 0!YlERTLIRATES John H. Epter, 11f. Janet,L. Polk 3.1 Methods. . . . .. . .. ........ .. ..... 66 3.1.1 Taxonomic Treat:ent . . . ... .......... ............ 87 3.1.2 Data Analysis . . . .. . .. .... .. .......... ..... 90 3.0 Results. . .. . . . . . .. . .............. . . . 32 3.2.1 Density .. .. . .. . .......... . ...... . 93 3.2.2 Biomass .. . . . . .... . .... . ... 91 3.2.3 Diversity (D) . . .. .. .. .. .... .. 91 3.2.4 l'ercent $1milarity Co-position. . . . . . . . .. ..... 91 3.2.5 Analysis of */ariance. . . . . .. . . . . .. ....... 91 3.3 Discussion . . . . . . . . ..... . . .. . .. ......... 97 4.0 AM31E:.T 'lATER CUAf IW 4.1 Methods. . ... . ... ... ... . .. . .. .. .. . . . 156 4.2 Results. . . . . . . . . .. ... .......... . .... ..... 156 4.2.1 PiliSICOCC!ICAL PARAM.ETERS. .. ..... . . ... . ....... .. . 156 Eric S. ::cClellan, Ja es 9. Scith 4.2.2 FECAL COLIFOR:1. . . . . . . . . . ..... ..... .. . 155 Linda :1. Wike 5.0 TtcRmL P1/.5 MAPP1:4 Ceorge A. :;ardacci 5.1 Methods. . . . . . . .. . ... . . . ................ 167 5.2 Rcsults. . . . . . .. ..... . ... . .. . . . 168 6.0 EFFECTS OF COOLI:C TOWER SALT 2RIIT ON ACRICL't.WRAL CROPS AND NATL'RAL VECETATION 6.1 PIA:.T FATHOCE 3 Ja=es D. !bnti;c erv, Robert F. Eppley, Jr., Lynn D. Wike 6.1.1 Methods . . . . . . . . . . . ...... .... . .. 19' 6.1.2 Ret te .. . .. .. . . ....... .. 145 6.1.3 och r 'Leetation Disturba ces . . ... . .. . . .. 196 6.2 QUA:. TIT; TI'iE VECCTATIW; EJJIES Ja:-es D. lbnti;o=ery, Lynn D. Wike 6.2.1 Methode .. . .. . . . . . . . . . 227 6.2.2 Results .. . . . . ... .. . . ..... 205 6.2.3 D1;cussion. . .. . ... . . . . . . . 212 t
1565 040
SCT!02 2.0 F158 O flQ i G,r;l s'
- - ' lil ,\ i j l,'
TABLES gO' ,,b l
Table Page 2.1 1 location of trapnet anJ seine stations. . . .. . . ....... ... .. !$
2.1 2 List of corswa and seeintific names of fishes taken by trapnet anJ seine during 1974 1975. and 19' in the Susquehanna River in the vict ity of TMINS. ... . ....... 19 2.2-1 Fishes taker by trapnet on 3-5 March 1976 in the vicinity of TM!NS. . . . . .... . 20 2.2 2 Fis'.es taken by trapnet on 15 17 March 1976 . 8. ....... . .... .... 20 2.0 3 Fishes taken by trapnet on 29-31 March 1976 . . . ..... .. .. .. .... 21 0.2-4 Fishes taken by t apnet on 13-15 Apr'1 1976 . . ...... ..... ... ... 21 2.2-5 fis' es taken by trapnet on 26-25 April 1976 . . . . . . . ..... ......... 22 0
2.2-6 Fishes taken by trapnet on 10-12 yaf 1976 ..... ... ............. 22 2.0 7 Fishes taken by traenet on 26-28 May 1976 . . . . . . . . . . ......... .... 23 2.2-8 Fishes taken by trapnet on 7-9 June 1976. . . . . . . . . . . . ............ 23 2.2 9 Fishes taken by trapnet on '9 June - 1 July 197t. .... ............ .. 24 2.2-10 Fishes taken by trapnet on 6-8 July 1976. . ......... .... ... .. 25 2.2 11 Fishes taken by trapne t on 19-21 July 1974. . . . . . . . . . . . . . . . . . . . . . . . 26 2.2 12 Fishes taken by trapnet on -& August 1976. . . . . . . ................. 27 2.2-13 Fishes taken by trapnet on 161S August 1976. . . . . . . . ..... ...... 23 2.2-14 Fishes taken by trapnet on 1-3 Septe ber 1976 . . . . . . . . . . . . . ....... :s 2.2-15 Fishes taken by trapnet on 33-15 Septe=ber 1976 . . . .. ............ 29 2.2-16 Fishes taken by trapnet on 27 29 Septeeber 1976 . . ..... .. ..... .... 3 2.!*17 Fishes taken by trapnet on 16 J October 1976 ..................... 3g 2.2-18 Fishes taken by trapnet on 25-27 cetober 1976 . . . . . . . . ........... 3t 2.2-19 Sunnary of fishes taken at trapnet station Ot-ACF-lA3 during 1976 . ......... 32 2.0-20 Suct:ary . . . . s tation TM-AQF-11A2. . . . . . . ........... .. .. ... 32 2.2 21 Sunsnary . . . . s t a t ion Ut- AQ F-11A3. . . . . . . . . . . . . . . . . . . . . . . . . . . . . 33 2.2-22 Sumary . . . . s ta t ion TM-AQF-932 . . . . . . . . . . . ................. 33 2.2-23 Sumary of fishn taken at trapnet stationa during March through October 1976 . . . ... 34 2.2-2a Nachly suse:ary of firhee taken at trapnet statir.s upstress (U) and downstress (D) from 33 the Discharge during March through October 1976 . . . . . . ... ...... ...
2.2-25 Indices of percent similarity of species compositten between trapnet stations during 1974, 1975, and 1976. . . . . . . . . . . . . . . . . .. .......
......., 36 2.2-26 Indices of percent similarity of species co= position between seine stations during 1974, 1975, and 1976. . . . . . . . . .. ....... .. ......... 36 2.2 27 Fishes taken by seine on 2 March 1976 in the wichire of Ut7!G. ... ......... 37 2.0-25 Fishes taket by seine on 15 Parch 1976. . ........... ... .. ... 37 2.2 29 Fishes taken by seine on 29 March 1976. . ..... ... . . .... .. 33 2.0-30 Fishes taken by seine on 13 April 1976. . ..... . . ..........
35 11 1565 041
. M.es ta'.es vi seine on 30 April tv76. . . . . . 39 2.2 31 Fis'.es !a.es te seine on 10 Pay 1976 .. . 39 2.2 32 .
Tis es ts en tv seine on 24 May 1976. . . . . . 39 2.2 33 . .
Fis%es ta.e, tv sein, on 7 June 1976. . . . 40 2.2 34 . .
. 40 2.2-35 Tis es takes be seine si 21 June 1976 . . .
fis%s ta.es by seine en 7 July 1976. . . . .. 41 2.2 30 .
2.2 37 is*e* ta'.es be seine on 19 July 1976 9 % ,. . .. 41 Hb' t .!.p uy , f,o (G. > ns e. taus be seine on : August tm. .- Yp a du dl {J f "
- .:-3s Tis es ta.es >y se tse on le August 1976 . ... 42 2.2-31 . .
Tasses takes be seine on 1 Septe-ber l's70 . .. ... 43 . 2.0-40 . fisies takes ty seine on 13 Septe=ber 1976. . . . 43 2.2*41 . Tistes taken be seine on 29 Septerter 19*6. . .. . 44 2.2 42 . . . a tisMs taken ty seine on 19 october 197e. . . . . (..' 2.0 43 . . . Fis es taien by seine on 25 cctober 1976. . . . .. . . 45 2.2*44 .. 3 cz:are f fishes taken at seine station 3-ACT 1 A: duttnc l's 7e .. . 46
-0.2*45 .
f e:x:arv . . station n:- AQF 16A1 . . . . .. 46 2.0-46 . .. . .
.. station T*.-AQF 10A2. .. .. . 47 0.0-47 i =r:are . ....
f == arv . . station W AQF-9Al ..... 47 2.0-48 . . . . . . . 2.0-49 ! .t:ra. e . ststian ?-AQF-953 . .. . . . . 46 2.2-50 5:=:are ef fishes taken at seine statists bring Parch through cetecer 1976 43 2.2-51 M: ste su=are of fishes taken at seine statians upstream (il) and downstreas (M f res the .tscaarge carir4 F.srch through' October 1973 . . . 49 2.2-52 c: Mitt:s f acters and reproductive status of channel catfish taken by trapnet durir.g
** arcs throup Wteber 1976 downstream (M ar.d upstrea:s (:') from the U:1N !ischarge . 30 2.2-53 C:Miti:s factors and reproductive statas of rock bass. . . 51 2.0-54 i:Mit ie: f actors and reproductive status of pu=pkinseed. . . . . 3:
2.2-55 C:Mities f actors and reproductive statas of white crappie. . . 53 2.2-56 (:Mities facters and reprodoctive status of blac's crappie. . . . . 54 2.0-5' (entities factors and reproductive status of spotta11 shiner. . .. 55 2.2-5d i:Mition fastors and reproductive status of spotfin shiner . . . . .. 56 2.2-5? s:Mities f acters and reproductive status of s%ite sucke . .
- .. .. . 56 2.2-60 Lescth f retaesce anJ eean weights per 5 ::: greur of fisbsa taken by trapnet on 3-5 Maren 197 4:mtream and upstream f rom the D'.1Xs 7,ischarge ... .. $7 2.2-61 tength freque?cy . . fishes taken by trap:et on 15-17 March 1976 . . . 57 2.2-62 le n ti trecaency ... fishes taken by tra;=et on 29-31 March 1976 5S 2.2-63 le gth fregeexy .... fishes taken by trepnet on 13-15 s.pril 1976 $3 2.2-64 le_gth f requency . fishes taken by trap:et on 26-28 .\pril 1476 .. . 59 2.2-65 te.cth fregaeacy ... fishes taken by trapnet on 1012 Y.ay 1976 . . .
60 111 1565 042
- 2. -66 tength frecaency . fishes taken by trapnet on 26-2$ yav 1970 . . .. . 61 2.0 67 Length f ree.ency .. fishes tak en by trapnet on 7-9 June 1970. el 2.0-6$ Length fre<aency .. fishes taken by trapnet on '9 June - 1 July 1976 b:
2.0-69 Length freque-icy .. fishes taken by trapnet en 6-s Jaly 197o. 63 2.0 70 Length freq.ency fishes taken by trapact on 19 :! July 1976. M
- 2. *71 Length f requ xy . fishes casen by trapnet on 2-4 August 1976. . e5 7.2 72 Length frecue9cy fishes taken by trapnet on 16-18 Au426t 197o. 66 2.0-73 Length freesency .. fishes taken by trapnet on 1-3 .sette .ber 19'o . 69 2.0-74 length frecuer . . (Istes taken tv t-aoner ca 13- 15 < e at -t e r 1976 . 97 2.0-75 Length f requency . . fishes taken by trap et on 27 29 septe-ter 1976 . 69 2.0 76 Length freteency fishes taken by trapnet on 18-20 Wtober 1976 ,
69
- 2. *77 Length fret;ency fishes teken by trapnet on 25-27 october 1976 e9 2.0-78 Length freq ency and : ean seights per 5 := -roup of fishes taken by seine on : March 1976 dos 9streas and systress fro = the TMI:s Discharge. . 70 a-2.0-79 Length frequency . fishes taken by setne en 15 varch l'70. . 70 2.2-60 Length f requency .. . fishes taken by seine onj9 March 1976. . . .. . 71 0.0-91 Length f recency . . fishes taken by 4eine on 13 Apft! 1976. 71 2.0-82 Length frequency .. fishes taken by seine on 30 April 1976. . . 72 2.*-53 Length frecuency fishes taken by seine on 10 May 1);s. . 7:
2.0 ?4 Length f recuency . fistes taken by seine on 24 May 1976. 73
- 2. -65 Length frecaency fishes taken by seine en 7 June 1976. . 73 2.2-86 Length fret ency fishes taket b se ne o. 21 June 1976 . .. . . 74 0.2-87 Length f recaency .. . fishes taken by seine on 7 July 1976. .. . . . 74 2.0 68 Luigth frequency fishes taken by seine on 19 July 1976 . . . 75 2.0-89 Length f requency .. fishes taken by seine on : August 1976. 76 2.0-90 Length feet.ency . fishes taken by seine on 16 August 1976 . . 77 2.0-91 Length frequency . . fishes taken by seine on 1 Septe=ter 1976 . 7d 2.2 92 Length frequency . fishes taken by seine on 13 septeder 1976. . . .. 79
- 2. *93 Length frequency . fishes taken by seine on 29 Septeder 1976. . . . 80
- 2. -94 Length frequency fishes taken by seine on 19 October 1976. . . 81
- 2. *95 Length frecaency .. fishes taken by seine on 25 October 1976. . . . 82 2.3-1 Su: mary of nu=ber of spect: ens, nu=ber of species, nuder of collection, and nu-ter rer collection of f'shes taken by trapnet and seine upstreas and devnstreas gros the DIEi Discharge curing 1974 through 1976. . 63 2.3 2 Kendall-cau correlation coefficients for species cor postrion at trapnet and seine stations during 1974-1975, 1974-1976, and 1975-1976 . . 84 FICt RE Figure 2.1 1 tocation of trapnet and seine stations in the vicinity of CI?G 85 m 1565 043 D
{wab filRffWlVJ v -. .a. uJ .a
$1CTim. 3.9 5%'1 tot ..u p l ut s 7A h Table 3.1-1 loss lon and Jescr.rtion of rarotsvertebrate stations. . . 17 3.1-2 Pacroinvertebrates ta' en f rom the auspehanna F1ver in t .e vic ;nity of Three "ile !stad 1-3.2-1 Nrbers and ettlura:.a of blouss, f us. :.f t enthic orun:s:s 7er Tocar gra5 (SM c=2' at station O!-AC -u!. Aprit l's76 . . 3.2 2 Nders a:.J =l!!!sta=a of bio-ass . at t d.i. n -" f41 1A1. :'ay D76. . *!. 3.2 3 N-bers and ettlic:a .s of bio-au at tatica P' A91-1A! . . e tv76 .. !!.
. 2- . Webers and mill: ara-s of bio _ ss at tati a f" AQI A1 aly 1*76 . ::.
3.2 5 %-lers and -111 tsras.s of bio ass at *tation N-AQi la!. A.r.st 1876 .M 3.2-6 %ders and =t!!ters.4 of blo ass .. a t totion N-i41-1A1 : erterker i s74. .- 3.2-7 Webers and =illicra s of bio ass .. at tatisa IP-AQI-1A1 <tsber 1976. .1-3.2-8 Wcters and'ailligra=s of bicrass at >tation "t-AQ1-1A2 > >rit D76. . .. 1;- at .tation -"-AQ1-1A;. Pa> 1976. ;;- 3.2 9 N-lers and mitt.ars=s of bio . ass , .. 3.2-10 W nbers and mil;tarass of bic in s at tation P'-AQ:-1A2. f.ne 1976 .. 3.2-11 2-ters and elitigrans of b!orass at -tation -AQ1-l'2 s .e: 1976 1;. 3.2 12 Nmbers and mi;.ista=s of bio ass at itation r*-AQI 1A2. A.g.st 1976 . .. 3.2-13 %-bers and =ill.gra-J of bio ass at r ation P'- Ay! 1A2. . eptert er 147s. ;.: at :tation 7t- A'<l 1A . ic tob er 19 76. . .;. 3.2-14 %=bers and =illista=s of biorass . at -tation 1:!-A;!-11A1. Arril 1976 !;! 3.2-15 %..bers and =tt!!gra-s of biorass . 3.2-16 W=bers anJ 111:pa=s of bio-ass at station r"-AQI-!!,1 : ay 117+ .:t at 5 tat ten P'- AQ:-11A1. Jane 1976. !;- 3.2 17 Nzbers and milligra=s of bio = ass . 3.2-18 %ders and milliga=s of biomass at -ta t ion O!-AQ1-11A1.1.ly 1476. . . ;.e at iration -'t-AQI-11A1. A.5 ast h76. ;;- 2.2 19 %ders and =L111&ra=s of biecass . 3.2-20 Aeters .nJ 1111pa=s of biomass ..at tation ~"-AQ1 11A1 Septe.ler 1976 . 1; 1mbers and =.1111pa-s of bio = ass . at 4:stion Ot-AQI-1!A1. Ntober 1916 n; 3.2-21 3.2-22 %=bers and =111tcra s of bio ass . at $tation *"-AQI-11A2 A?ril 1970 . !?; 3.2-23 %ders and =t111pa=s of blouss at station Pt AQI-11A.'. P.sy 1976 . n3 3.*-24 W W.rs and =t111pa=s of blocass at itation !" Aqi-11A hae 1976. 1, 3.2-25 N !,ers and milliga= . of biomass . .. at itation D! AQ1 11A ? Lly 1976. . .. 13 3.2-26 Nders and eill!pa=s of bio ass at station Ut-Aq1-11A2 A.gs.st 1976. . .2-3.2-27 Webers and milliga=s of binass at ita:Lon P! AQ1-11A2. septe=ber 1976 11* at -tation Ut-AQL-11A2. u tober 1976 ;- 3.2-25 Webers and millina-s of bio-ass .
%ders and mit!ipau of biorass at tation n!-AQI-E1 April 1976. . 12 a 3.2-29 at st ation *"- AQ1-931. Pay lif e. ..
3.2-30 habers and astliga=s of biomass . 3.2-31 W::eers and stilizrams of bio-ass . at station 7"- LQ1-9!1, hne 1970 . :.-
%ebers and nitlicra-s of *otouss at Station 01-AQ1-911 .'.ly 1970 ..;
3.2-32 . V b h [] Q; U (j pU sI wput Udlljh ! b n 1565 044
3.2 33 N ters and milligra _a of bio-ass , at 4tstion !"-tQt-9'.1. August 14 4 la 3.0-3; %afers and sittigrams cf biorass . . at itat ion 7*- AQ t-9st. serre-Nr 1 *7a. 1.. 3.0 35 %=Sers and alltitra .s et blocass .. at statten T*:-AQ1-4al. October 1#7*,. . 1;, 3.2 b 1=Sers and percent caposition of benthic organte .s collecteJ at the e.ast.unvert e rate stations. April t5 routs ivtober 1770. . . teo 3.:-37 Estt=ates of density s nu=ber/e: e of the do=inant taxa at the esc rainvertebr ate statto,.. Aprt! throart October 1970. . . . . . . . . 1;* 3.2 3s Isti-ate of bio-ass ( s /s2) of the dominant taxa at the e.ac-oinverteOrate stations. April thr;uG October I A70. . . . 1.9 3.2*31 31versity (D) values at the eacroinvertebrate stations. Apt t! throuth W eeber l oin. 1;s 3.2*40 Indices of percent si.-ilarity of species co=.wsition (lye t between the -JcroiwerteSr.ite stations sa_ pled Aptt! throuc% Octaber 1974 1773. anJ 197b . . . 1;3 3.2-41 Analvsta of variance. rende-tred bloc's design for nt--ber . of taxa. Apett throach %toler 1976. . . . . . . . . . . . . . . . # . 1.s 3.0 42 Ce=parison of rean nu=cer of taxa at the acrotnvertebrate stations usinc student !.e.-:.an-Aeuls esaltirange test. April ttrhr,% October 1976 . . . . . . . . . !;* 3.2-43 C.* parison of =ean s :ber of tana by sa pting date U.*ril through octd e* 1976) . sing
$tudent* Wm-f euls -adeirande test . . . .. . . 1 *. 9 3.2-44' Three-facter 49alysis of variance for densities of f f-Wrilog t'off-eteteri at tue FJcrotnvertebrate stations. !*ay through t\ torer 1974 through 1876 . . 15) 3.2*a5 re parison of lorartt'=le 9ean density of f t--Mrit o. Mf fra t 9ter t by year (*Jy through October 1974 197tn astP4 Student =:.ev sweuls ruit trange test ... 159 3.2-46 C:=sarison of logartt :1.c cean density of f.1-aMrting haff eleteri by sa9; ling date C'sy through October 1974-1s76) usiag Ftudent-?;ev=.an e euis :ultirenze test . 150
- 3. *?7 Cc parison of logarit=le =aan de alty o f ' f-e f-i t'.9 h*ff efatert at t'e =acroinverte-brate stations us teg student-::ev .an-keuls =ultirange est. :# y throu;% t c tater t r74-1779. 150 3.3 1 5.=2:ary of data collected at the =acrotnvertebrate sea .Lons for 1974. 1975. a s 137e. 151 FIC'JRES Figure 3.1-1 fecation of benthic _acroinvertebrate stations in ene vicinity of Utt:5 . 15?
3.0-1 Percenc ce= position ef -acrotsvertebrate taxa. based on the total nu=ber of in*1viduals collected at the =acroinvertebrate stations. April throur,5 october 1970 . .. . 15) 3.3 1 Wrters at taxa taken at tha macroinvertebrate stati?ns. April throug% October 1876 154 3.3-2 Siversity (D) values at e.acrotnvertebrate stations. Apf t1 through october 1974, 197:. and 1976. .. . . . . . . .. ... . . 155 A.".,IE :: *'ATER Qt*EITY SECT 105 4.2 D**D
~ ~
*@ fli.
l L. V Lj 3 j
^ "
table dd J _k a 4.1 1 Para =eter. =ethod used, and reference for analysis of water taaen in the vicinity of
!"1?5 in 1970 . . . . IfJ a.2-1 Mc?.thly =ean. =ini: .m. and ramicus concentrations of selecteJ water quality para:eters taken in the vicinity of 5 1:3 in 1976. . . 1:1 4.2-2 : u rars of selected p*tysicoche=ic al para =eters take=t on 6 and 20 April 1974, in the vic inity of 7"!!2 . . . . . . If2 4.2-3 Su z:ary . on 4 aM 16 Pay 1970 . . . . . tg; vi 1565 045
.. - 1* s
- 4. ' 4 t umar/ on 1 aaJ l' .Nne 1@. .
. . te,
- 4. 5 S u-ra ry . an g and .'o f at y 197s. .
1(. on 3 ani 17 August life. 4.0 9 suma r/ . . l ,. 4.:-7 urr.a t .- na 7 and 21 eptiM er 1976 . . .. .
. . . 1.'
4.0-8 5utcarv . . . on 5 anJ 19 ist.Aer 1)?e . 4.2 9 roedinations ut five consemstve sa: ples f or deter-ination c f ti e rea etr:t'stea. cf .te.a:
- collfors density at ar.51=st unter q.a}:t statt.me. A;rt! t..rv.e ecte er 9 i 7f.i's 5.0 ::1:3* T' e'5- ?ni p t*r.
9@ f][i[f)I Q[ i T A') S a ~ 4 , 17;. 5.:-L it.er-al plu a data f or 7:*!!;. On it retr.ary 1976. . . . .
.. . .. . 171 5.:-2 TI er al plu_e data f or *::!:.5 on 29 : =t ruary tvi6. . .
. .. . .. 17 5.0-1 f t.er-41 pla a dat a f or ** !?; on 21.etri.arv 1176. . .
- e. . . ....... 173 5.2 4 Ther.at pl ee data for':'t*: 3 on 21 Tetruary 1976. . . .
. . . 17.
5.2 5 Ther .at plee data f or T"!:3 on 21 Iebruary 1976. . . .. .
. . .. . . 175 5.0-6 Ther-al pler-e data f or T!!!:.3 on 21 Febr.ary 1976. . .. .
. . .... 17e Ther .nl plu=e data for I"!::S on 21 rettuary 1976.
5.0 7
. . 17" 5.2 4 Ther-al plu a data for t't!;. on 21 febrJ1TV 19I6. . . . .. ..
.. 173 5.2-4 !5er-21 plu== data f or 7*:1:3 on 21 February 1974. . . . . . . .
.. 17
%.2 10 Ther-41 plu-e data for T"1::3 on 21 r ebruary 1976. . . . . .
75ernal plce data for O!!!:S on 21 ebruary 1976. . .. . ........In 5.:-11 Ther=at plu=e data for 7*:1?G on : Tet rta ry 1979. . . . . . . .. . . 11 5.0-1 T?.er=al plume data for I:1!:s on 23 retruary 1974. . .. . . . 13: 5.2 13 Ther al pine data for T*.:lis on 5 " arch 1976. . . . . . 13) 5 -14 Ther 41 p1 tree data for TMI:s on 19 :* arch 1)?6 . . . .. 11 5.2-15 Ther-41 plee dace f or T? 1?ss on 1 Apell 1976. . . . In 5.2-16 5.2-17 % ernal plu=e fata for ttt!:S en 15 April 1976 . . . . .. t-5.2-18 Ther=al plu=e data for T!!!!5 on 29 April 1976 . . . 5.2-19 Ther=al plu=e data for T'itNS on 13 ay 1976 . . . . 5.2-20 Ther 41 plu=e data for 5:1?;5 on 27 a : y 197a . . . . .. . . 1..
- 5. -21 Ther=al plu=e data for ??:t N on : Jane 1976 . . ..
3er-al plu=e data for T? 1::s on 10 Ju=e 1976. . . .. .. . 1-
- 5. -:
Tbersal plu=e data for T:1?:S on :* June 1976. . . . . 17 5.2-23 1.. 5.2-24 3er=al plee data for n!I?:S on 15 July 1976. . . 1
- 5. -25 711ernal plu-o data for 17:1 3 on 3 A!y 1976. . .
ner al plu=e data for !!' INS on 1: Agust 1976. .. . 1-4
- 5. -26 .
Thersal plume data for !!!!: . on :$ Au.tust 1976. . . . . . 1s. 5.2-27 vil 1565 046
5.2-28 Thermal plu-w data for T.'1*.3 on 9 September 1976. . .. . . IN 5.2-29 Ther J1 plume data for TMt!.s on 22 8cpte-ber 1470 . . . 1H 5.2-30 ISer=al plu=e data for ??t!!;S on 7 October 1970. . . . 171 5.2- n Ther=al plure data for TMin on 21 os tober 1976 . . 5.2-32 Ther=al plu=e data for f.1:s on a Lve-ber 1870 . ... . . .. 5.2-33 Thermal plume data for n:1:e5 on 16 :ovember 1976. . . . . 192
.s 5.2-24 ser:ary of surf ace water te veratares at selected plu:-e rap stations, disdaree and a-6 tent river treperature dif fere..ces, air te perat ares, winJ conditics. Jincharge rate, river flav, anJ station operation level f ebruary throue Lve-ber 1976. .. . . l'J 3 SECT 105 6.0 EFFECT3 or Coell C TLNER SA1.T OR!!"r 0*i ACR!CU1.TtUL i KOPS A:.3 ::ATtTX., 'lLCETATIO :
6.1 PIN!! PAT 90CE:;5 TABLE $ Table 6.1-1 Fiants observed in flower in salt drif t transects in the vicinity of T!:!!s in 1976. . . 197 6.1-2 Parasitic plant Jiseases observed on agricultural crops in plant pathology transects, a - April throug4 October 1976. . . . . . . . . 203 6.1-3 Farasitic plant disenscs cbserved on natural vegetation in plant pathology transects, April througn october 1970. . . .. . .. .. . 204 6.1-4 Yegetatios exhibittra significant insect da: age in plant pathology tsar. sects, April through October 1976. . .... . ... . . 205 FICf.RE Figure 6.1 - 1 Location of salt driat transects and areas of quantitative vegetation stady, in the vicinity of D:I:s . . . .. . . ... ... 206 SECT 1016.2 Qt A::!ITATIVE YECETATIO!; STOIES q n lhU TABLE 3 . b Table 6.2-1 Co=parisoa of trees and samlings on 24 selected plots in the bottomland harc.-ood forest as Shelley Island, 1973-1976. ... . . . .... ... ....... . 214 6.2-2 Co=parison of shrubs and vines on 24 selected plots .n the bottomland hardwood forest on Shelley Island, 1973-1976 . . . . .. . . ..... . . . 215 6.2-3 Cround cover eccurring in the totto-J1and harduced forest on Shelley Island,1376. .. 216 6.2-4 Co parison of dominant ground cover occurring in the botrosland hardwood forest on Shelley Island, 1973 1976 . . ... . .. 217 6.2-5 Tree seedlings in bottomland harducod forest on the11ey Island, 1974,1975, and 1976. * . 217 6.2-6 Co parison of trees and septings on 17 selected plots in the south forest er. Three : lite Island, 1973-1976 . .. . . . . 218 6.2-7 Co=parison of shrubs and vines on 17 selected plots in the south forest on Three !!!!e Island, 1973-1976 . . . . . . . . ... 213 6.2 8 Cround cover occurring in the " vine" portion of the black locust forest on ~ntee 2:ile Island, 1376. . . . . ... . . . . . 219 6.2-9 Co=oarison of the dominant ground cover occurring in the " vine'* portion of the south woodlot on Three Mile Is!and, 1973-1976 . . .. 220 viii 1565 047
6.2-10 Tree seedi tnc e in t'.e " vine ** port ion o f the t, lac it loc us t f orest on 't ree Mite Island, 1973-1476 . . . . . . . 220 6.2 11 cround cover occurring in the "non-vine" portion of ti black locust forest e9 Three Mile Island, 1976. . . . . . . . . 221 6.2 12 t emparison of t*e dastnaat ground cover occurrin4 in the "non vine ' portion of the south woodlot on *tre e " tie Island, 1973 1976 . . .. . .22 6.2-13 Tree seedlines in the "non vice" portion af the black locust torest en Three "ile Island, 1973, 1975, eM life. . . . . . . .': 6.2 14 Cround cover occurries in the saath !! eld on tree "fle Icland, I 'v 7 6. '
. . 2'3
- 6. 2- l', rowarison cf d.*_inant ground cover occurrir4 in the south field on Three Mile Island, 1973 1976 .
22. 6.2-1b Tree seedlings is the south field on Three "11e Island, *a973-1976 ... 6.2 17 cround cover ucc rring in the field near the south ponds on Three ,11e Island,1976 .;1 6.'-18 Co parison of Micant ground cover occurring in the field :: ear the south po-ts en Three File Island, 1673 1176. . . . . . ... . . .. 2;6 6.2 11 Tree sedd11ngs in the field near the south ponds on Three Mile Island,1976 . . 226
- 6. 2 2') Cround cover occurring in the north field on Three Mile IslanJ. 1976. . .. 2*?
6.2 21 co parison of the da:Inant around cover occurring in the north fleid on Three : tile
- s t and,1* 73 197o . . . . . . . . . 226 6.2 12 tree seed!!rgs in the north field on ihree ile " stand, 1973-1976 .. .. 22) 6.2 23 Ground cover occurrieg in the field near ti e 190 kw s abstation,1774. . .... *2a 6.2 2; re=parison of *he da:Inant grosnd cover occurriag is the field near the 500 kv sutstation on Route 441, iki.-1776 . . . . . 231 6.2-25 Tree seeditnse is tr.e field near the 500 kv sutstation, 1974-1976 . . .. 231
_uo- a 1 ix 1565 048
O .
][l O r : s ,,
p cav.:: n'r. 'v'.T;
*'e wish to thank Barbara reck, !!!chael Surint, Tho: as Anckes, tud Yoch, Ja es Mudge, John Recanski, and James 6ta ey of "etropolitan Edison Co:pany for their assistance in the past year. We also appreciate the help of Three Mile Island !!uclear Station Security without whose assistance our work wuld haie been impossible.
- The following biologists participated in the study in 1976:
John Epler, Robert Eppley, Richard F. vans !!arold i~agerty, Barbara L.1throp, Robert Palick, Eric "cClellan, Ja=es !'ontcocerf, Cecrge ::ardacci, Janet Polk,
'a'ayne Fotter, Philip Ritson, Ja:es Smith, Walter soya, t.inda Wike, and Lynn .'ike.
, Linda .*ike provided secreer.rtal services and assistance. We would also like to acknowledge the follewing specialists for their advice and assistance in confirning the cerfor=ing deter-inations: Dr. Marvin L. Bobb (flemiptera), "r. Jarl K. Ifiltunen (Tubificidae), Mr. Michael S. loden Claididae), 'r. Tho=as P. Poe (Ilirudicea), Dr. John W.
?.eyrzalds ("egadriles), Dr. Selwyn S. Reback (Chironomidae), Dr. Ole A.
Saether (Chironomidae), !!r. Clark ::. Shiffer (Odonata). Others who assisted in providing help incle.fe: Dr. Robert enoncourt, the Pennsylvania Fish Co raission and a special thanks to Dr. Cuy L. Steucek (Mill .rsville State College) and Jeffery J. !!ando (Ichthyological Associates, Inc., Absecon, N.J.) for their statistical advice. 1565 049 X
1 1.0 ! *-' ' "r T io" This d:c =ent is the third annual postoperattunal report on the ecology of York Itave.1 Pond (Lake frederic), Susquehanna ".iver, Pennsylvania in t:ie
- Inity of the Tnree i:11e Island 'hclear station (T*!!!;S). Ichthyological 4ssociates x . initiated the study in February 1971.. Unis report covers the period fres January through Dece ber 1976. Sections are presented to ceet the O:virort ental Technical Specifications (ETS) for T:!I ;5, Unit 1, ,
Appendix L. Para eters analyzed are the sa u as reported in Potter and Associates (1976) with the exception of Lepingerent of fisher, entrainment of ichthye;!ankton, entrain: cut of plankton (phytoplankton and rooplankton), and bird i:: action on cooling tovers. The ETS requirements for surveillance of these para xters *rere fulfilled and the programs were ter=inated. Die 21:5 t'ntt I acuteved critic.ility on 5 June 197t.. L' nit I has been at v u lous levels of operation ranging f rom corp 1;te shutdova to 1007., 230 regawatts. *n 1976, the T::1 :S Unit I was shutdown for refueling from 21 February t.' 27 "ay. Potter. ..A. and Associates. 1976. An ecological study of the Sust;uenanna River in the vicinity of the Three !!ile Island !;uclear Station. Annual Report for 1975. Ichthyolegical Associates , Inc. 395 pp. D'D WV6 [ D ooJ eJ b jN _a 1565 050
[j ) r! - . 1.1 n"'.m 1.1.1 Fish . Fishes were sa= pled at four tra;ne; am.d five sei stations, " arch through October 1776. " A total of IL4 tra:=et collecti:=s yielded 822 fish of 25 species. The pu=pkinseed and cha==e1 catfish ve e ost abundant. Comon fishes were taken in eg:41 or greate.: -_=bers 4:restream from the Discharge than
, upstream. !;o sienifics== change in s;ecies rank at individual stations was observed from 1974 c:::;gh 1976.
A total of 9') sei=e collections yie;ded 10,478 fish of 35 species. The spottail shiter ra ied first in :Tarall abundance and was the ex)st co:rxan species at all s:ations. v.o s: :mn species shoved nearly equai distribution a:c::3 eps:reas and dov _st e.z: stations. Significant Jifferer.ces in species rar.k at one upstream and one 4:r.rnstream station were observed between 1975 and 1975. 2;o appreciable differences were :2::ed in condition factor or weights dovnstrea= and upstrea: from the Disch.a ge where sufficient. nu=')ers were present; =est values were within the ra=ges observed in previous years. The fish leech, 'a-tedella Int-n 's, and anchor .c: s (f.ernaea spp. ) were co:rzan ectopara. sites. Variatio:.s is fish abundance may :e attributable to year class fluctuatio:s. Se 1::;4:: of T1!I;S Cri: 1 on fishes was negligible. 1565 051
oo n . _. 3 D D l M af h $ 0LUjdy g 1.1.2 !!ac ro inver t e.b rate s
!!acroinvertebrate collections were taker. se.i:nonthly April through "ctober 1976. A total of 90,567 tpect= ens representing 112 taxa was taken. ' !--no d r il u s ha t' f re f = t e r i , ' k i -a n =. .' - ,r :s , a-.4 *:a i s clin; :is vare the ost abundar.: taxa. t.!--nodrilu h:f fraisteri was usually :ncst abundant at all stations each month, conf o' as is virrinic a, L. hof t'rei steri, and .
C.. deenros had the greacest bio = ass of all specimens weighed. 1:enthly esti=ates of diversity ranged f rt: 0.66 to ,2.76. Iedex of percent similarity valets between stations were in the inter ediate to high af finity range (> 50". sisilarity). liigh si:11arities in species co: position vere found between Station lA2 and 931 (91*.), and llAl and llA2 (89*.). Comparison of nu-ber of taxa between acroi:wertebrate stations and sa=ple dates for 1976 was acco: plished by analysis a f var: snee, tandocized block design. The Student-::ew .an-reuls :ultira:ge test revealed that Stations IA2 and 9B1 a:sd llAl,11A2, anj 931 sare si ilar in nu:.ber of taxa. Three-factor analysis of var.ance perforced on densities os 1.!-redritus haf frelsteri ".ay through October 197/. chroe:;51976 revealed that years, ca ple dates, and stations were significantly dif f erent. The :nacroinvirtebrate enrr= unities appeared to be r-cre af fected by ice and high river flov than by the operation of TS:3. 1565 052 b
I i 1.1.3 Arbient 'iater Quality ' (,; '
.1
-o1 ; , ' jJ
.1.3.1 Physicocnemic41 Para =eters Except for dissolved oxygen and total suspended solids the conthly istribution of :arameters was similar. ?!can values wera high in September
.ad law in Apr'.1 and 3:ay. The no ichly mean concentrations of cost parameters
.: Station 11A1 (n: INS Discharge) were generally higher than at the other *
- ations.
.1.3.2 Fecal Colitorm The highest averall nean density of fecal coliform was at Station 1A1; the lowest was at Station 11A1 (n! INS Discharge). :enthly cean fecal .:oliform densities sere lowest in April, increased throughout the su=.er, and peaked in Septe=ber. For all stations the geometric =ean of fecal co1Lfor 2 densities Cycended the limit established for the Co:mwealth of Pennsylvania. ,
1.1. '.
- Thereal Plume !! apt ,9g Thirty-three plume surveys were conducted at various river flow conditions and station operation levels. The discharge te=peratures were within the limits established in the ETS. A return of the discharge temperature to within 2.7 C of anbient was used to define the plu=e.
In S of 33 surveys the plume was limited to 5 m offshore and 25 m downstream from the Discharge. 1565 053
j t h .: analytical plu=e model for norul coolcovn conditions was compared with the cooldown for refueling on 21 February. The pluce was recorded no further than 20 m offshore and 10a0 n downstrea:s from the Discharge. This varics from the predicted model presented in the environmental state:nent for the operation of T:!I::S. !!igh river flow during the cooldown operations may account for this variance. 1.1.5 Effects of Cooling Tc,wer Salt Drif t on Agricultural crops and Natural Vegetation 1.1.5.1 Plant Pathogens e Plant pathology transects were examined from April through October 197/- :o differences were noted in
- flowering time or appearance of the 219 taxa observel with respect to the location of possible salt drift.
Plant parasitic diseases were found on four agricultural crops and 21 taxa of natural vegetation, and insect damage was nnted on nine taxa. ::one of the damage caused significant defoliation and no pattern was observed relative to the operation of the cooling towers at T!!I:5. 1.1.5.2 Quantitative vegetation Studies Two forests and four fields were surveyed late August througit mid-October 1976; results were statistically compared with those obtained in 1973 and 1975. There were few changes in the overstory and understory in the fe.ests. Soce of the statistically significant changes in ground cover in forests and fields were related to natural or hu=an disturbance; others were normal in the course of secondary succession. No pattern of change was found that was attributed to the operation of the cooling towers at T!!I:5. 1565 054
2.0 FTSM The ETS, Appendix B, Section 4.1.1D requires replicate fish sa=ples be taken both inside and outside of the thermal plume every t-v veeks, March through October. oq ggg _ W J 3 2.1 ?TTFMS Fish were saepted every two weeks at four trapnet and five seine stations, l'. arch
- through October 1976 (Table 2.1-1 and Figure 2.1-1). High river flows during June and October necessitated collectiots be taken on s seceeding wee'ks. Trapnet collections taken on 29 June through 1 July were -
analyzed as June data. Habitat dif ferences in water velocity, depth, substrate, and available cover were observed at the stations. Riffles were noted at the upstream seine stations during low river flow; no rif fles were encountered downstrea=. Mud and silt were comon substrates downstream while mud, rubble, and boulders predo inated upstream. Rubble, boulders, and vegetation provided limited cover. k'ater depths ranged to 2 m. Fishes taken by trapnet and seine since 1974 are listed in Table 2.1-2. Comon and scientific names and taxonomic order of presentation followed Bailey et al. (1970). References used for fish identification included Denoncourt (1975), Gibbs (1957) Hubbs and 1.agler (1964), Pflieger (1975), Scott and Crosscan (1973), Snelson (1968), and Trautran (1957). 1565 055
Identification of young of the white sucker from those of the shorthead redhorse was dif ficult. Young vere distinguishable only upon internal examination of gas bladder chambers. Therefore, specimens were listed as white sucker /shorchead redhorse until ther were large enough to be identified by external characteristics. Condition factor (K) for fishes co=prising more than 107. of the trapnet or seine catch during 197!.. 1975, or 1976 was calculated using the formula: K = 100W/L3 where u = mean weight (g) per 5 en group, and L = upper limit of 5 emi fork length interval expressed in cm. Species diversity indices (D) were calculated for each trapnet and seine station using the Shannon-Weaver function presented by Lloyd et al. (1968): D = C/N(N1og10N - { niloggno t) where C = 3.321928 (converts base 10 log to base 2), N = total number of individuals, and nt = total number of individuals in the ich species. An index was computed to identify the percent similarity between stations with respect to composition of fishes (Whittaker and Fairbanks 1958). It was expressed as: PSc = [ min (a,b) where PSc = the percent similarity and a and b = the percentages of a species in samples A and B. PSc values range from 0.0 (no similarity) to 100.0 (complete similarity). This index measures relative si=ilarity in terms of species populations and often leads to grouping of co=: unities by dominants or major species. c ' :. i Q QY \
$50 6 1565 056
3 Kendalt's coefficient of rank correlation (Sokal and Rohlf 1973) was applied to the catch data to analyze the yearly variation in rankings of species at a station. This did not test whether numbers collected in different years were significantly differt.it, only whether their respective rankings were correlated (Suc=erfelt and Minckley 1969). Physicochemical data included ti=e, weather, secchi disc, and air and vater te=peratures. Dissolved oxygen concentration and pH were detemined froc vater ca..ples taken at each station. River stage was obtained from the Earrisburg River Cauge Station for 0700 hr. Data for traonet catches were presented as two, separate 24-hr collections. Mini =um valut.* for para =eters were listed first regardless of collection date. Single recordings for a pa a=eter indicate identical observations throughout the period. Each trapnet consisted of a 0.91 m by 15.24 m lead net and a 0.91 m by 1.83 m metal fra=e connected to t o traps (4, 0.76 m diameter hoops). he lead net and trapnet vere of 1.27 cm mesh. ::ets were set for 24-hr, were checked, and reset for a second 24-hr period. Effort was cade to set nets perpendicular to shore; however, high flows of ten caused nets to be set at angles of 45 degrees or less to shore to prevent rolling. Fishes were identified, measured, weighed, and released in the field. A 3.05 m by 1.22 m seine with 0.32 cm eesh was used; at least three hauls were made for each collection. Additional hauls were taken when further effort might alter the relative abundance of fishes or yield other species. Fishes were preserved in 10". formalin for one week, rinsed in water and let stand for two days, and stored in 40". Isopropanol. om craha[ g D D "e ~ N' 00 h0ME K N' _a 1565 057
9 Specimens were ceasu ed to within a 5 r=s fork length interval. All fish of a species within the same interval in each collection were weighed to the nearest 0.1 g. A subsa=ple was measured and weighed when a large nu=ber e (100+) of one species was taken in a collection. Reproductive status for fishes was defined as follows: young were spawned during the current calendar year; ju entles were incapable of e reproduction, or minnows anu darters les; than 26 =m collected prior to the current spawning season; and adults were capable of reproduction. Classifications were based on field observations and infor=ation in the literature (Carlander 1953, 1969; Miller and Buss 1963; Scott and Crossran 1973; Trautman 1957). Fishes were examined for ectoparasites. 2.2 RESULT 9 - 2.2.1 TRA PN'ET Results of March through October trapnet collections are reported in Tables 2.2-1 through 2.2-13 and are su ari:ed in Tables 2.2-19 through 2.2-24. A total of 144 trapnet collections (36 upstream from the Discharge and 108 downstrem) yielded 822 fish of 25 species (Tables 2.2-23 and 2.2-24). Most fish (295) and most~ species (20) were taken at Stations 1A3 and 11A2, respectively. The number of specimens per collection (n/ Coll.) was 8.19 upstream and 4.88 downstream (Table 2.2-24). Except for the white sucker and northern hog sucker, all species were taken in equal or greater nu bers downstream. Catch per month was greatest at three of the four stations (IA3, 11A2, 9B2) in September (Tabics 2.2-19 through 2.2-22). 1565 058
10 Sunfishes and catfishes dominated the catch. The five most abundant fishes (74.57. of the total catch) were the ~.:=pkinseed, channel catfish, rock bass, black crappie, and redbreast sunfish (Table 2.2-23). Nine sunfishes comprised 62.57. of the trapnet catch. T,he pu=pki= seed ranked first in overall abundance (26.0') and was the cost corr.cn species at Stations 1A3 and 932 (Table 2.2-23). Other sunfishes that comprised = ore
- than 5.07, of the catch were the rock bass (11.7*.), blsek crappie (10.1*.),
and redbreast sunfish (8.67.). . Five. catfishes accounted for 25.17. of the catch; slightly greater nu=bers were taken downstream (Table 2.2-24). The channel catfish (18.1".) and brown bullhead (5.07.) were cost coc=en. Two juvenile alewife were captured at Station 922 on 13-14 Septe=her (Table 2.2-15). This species had not been recorded from the lower Susquehanna drainage in Pennsylvania sir.ce the 1930's (Fowler 1940). Introductions were made in 1969 into i=pou+=nts in the Susquehanna watershed in Centre, Columbia, and Luzerne counties (Robert B. Hesser, Pennsylvania Fish Commission, personal co=unication). The speci:. ens ay have migrated downstream from one of these i= pound =ents. Other fishes taken for the first ti=e by trapnet included the cuskellunge, northern hog sucker, yellow perch, and valleye. Four species previously taken by trapnet, the goldfish, bluntnose mi mow, falifish, and tesse11ated darter were not collected in 1976. 1565 059'
11 oo , 3npr ao o Diversity indices calculated from su =ary data for each station ranged from 2.95 (IA3) to 3.35 (11A2) Table 2.2-23. 1onthly 1;. dices at most stations peaked in July or August and ranged f ro= 0.00 at 11A3 in October to 3.24 at 11A2 in August (Tables 2.2-19 through 2.2-22). Lower diversity indices reflected the do=inance of a single species. Percent si=ilarity indices between stations were moderate (Tab *.e. 2.2-25). The greatest si=ilaritf (71.2) was between Stations 1A3 and 11A2; it was caused by the dominance of the channel catfish and rock bass. The similarity between Stations IA3 and 932 (66.1) was characterized by like habitats and dominance by the pu=pkinseed. The least similarity of 49.4, betseen Stations 11A3 and 932, was caused by dissi=ila habitats and the absence of coc=mn dominant species. 2.2.2 OEIE Results of !! arch through October seine collections for each date are presented in Tables 2.2-27 through 2.2-44 and are su==arized in Tables 2.2-45 through 2.2-51. A total of 90 collections (36 upstream from the Discharge and 54 downstrea=) yielded 10,478 fish of 35 species (Tables 2.2-50 and 2.2-51). 1:ost fish (2,%5) and =est species (29) were taken at Stations 1A2 and 16A1, respectively. The nu=bers of specimens per collection upstream and downstream were co= parable (136.50 and 103.04, respectively). 1:os t dominant species shoved nearly equal distribution among upstream and downstream stations. 1565 060
12 Seine catches were s=all and erratic from March through .ay; only 48 specimens were collected in May (Table 2.2-51). The catch reached a peak in June (3,611 fish) and corresponded with a large spawn of the spottail shiner. Catches at all stations except 1A2 decreased during July and August. A secondary peak of 2,050 fish was recorded in September when young of the spotfin shiner were abundant. The number of specimens per collection was si=.ilar at all stations except 9Al"(rable 2.2-50). Fewest fish (1,006) and least species (19) were taken at Station 9A1. Sciaes were difficult . to fish at Station 9Al because of boulders and deep mud. The spottail shiner co= prised 52.77. of the catch and was the most shim +t species at all stations (Table 2.2-50). The spotfin shiner ranked second in overall abundance (19.8".); nearly half of the speci= ens were taken at Station 1A2. Young of the white sucker /shorthead redhorse accounted fer 6.7*. of the catch and were most co=mn at Station 16A1. The tesse11ated darter ranked fourth in overall abundance (6.57.) and was cost co==on in Septe=ber. Young of the channel catfish ranked fifth in overall abundance (4.7",); t: ore than 997. were taken downstream from the Discharge (Table 2.2-51). Fishes taken for the first ti=e from the study area by seine included the fathead minnov, yellow bullhead, and shield darter. The yellow perch was the only species taken in previous years not collected in 1976. Overall station diversity indices were low due to dominance by the spottail shiner and spotfin shiner and ranged from 1.75 (1A2) to 2.45 (10A2) Table 2.2-50. The highest monthly index (2.71) occurred at Station IA2 in August (Table 2.2-45). oqgo rh@d}6'> 1565 061
13 Percent si=ilarity indices between stations were high (Table 2.2-26). The greatest si=ilarity (82.C) occurred between downstret,= Stations 10A2 and 9A1. The lowest si=ilarity (%.t.) was found between the two upstrea= stations,1A2 and 16A1, and resulted fro = dif ferences im abundance of the spotfin shiner and suckers. St=ilarities between upstrea= and devnstres= stations were reduced by the unequal distribution of the channel catfish. Si=ilarities seemed less dependent on the presence of like habitats and more dependent on affinities of do=inant species. 2.2.3 REPRoycTIVE e,TATM A?.m catTTION ~XTOR Reproductive status and condition factor (K) per 5 rc fork length interval for the channel catfish, rock bass, pu=pkinseed, white crappie, and black crappie taken by trapnet and the spottail shiner, spotfin shiner, and white sucker taken by seine are presented in Tables 2.2-52 through 2.2-59.
.Mean weights per 5 =n fork length intervals of fishes taken by trapnet and seine are given in Tables 2.2-M through 2.2-95.
Juvenile channel catfish were co=non in trapnet catches during " arch, April, September, and October; ost adults were taken in October. Young channel catfish first appeared in seine catches on 7 July; this =ay indicate that spawning began in. June. Most rock bass taken by trapnet were adults. Ripe cale and female pu=pkinseed were co =nn in June and July trapnet catches. Young of the white crappie and black crappie vere taken by trapnet in September. g 0 h 1565 062
l
' , ol
!bst spottail shiners taken by seine were young or juvenile; young were first collected in June. Spottails spa ned in May ar i June grew to 50-60 :n F1. by October. The spotfin shiner appeared to have an extended spawning season with peaks in June and August. *' . inter survival of young spotfins of the 1975 year class was good as indicated by the abundance of
~ juveniles in spring 1976 seine catches. I'ost white suckers spawned in June; young were com on in July seine catches. - No appreciable differe=ces were noted in condition factors or weights downstream and upstreas from the Discharge where sufficie,nt nu=bers were present; :ost values were within the ranges observed in previous years.
~
2.2.4 PARASIN 5 The fish leech, Wrobdet t a 19eubris, was a co=:non parasite of the tesse11ated darter. Infestation on darters was first observed in August and reached a peak in October. Some darters were parasiti:ed by up to five leeches. The site cl attach =ent was always on or near a fin. !b parasitized darters s= aller than 31 en were observed. One adult channel catfish was also parasitized. M. lugubrig shows the greatest distribution of any piscicolid reported in brth America (ifugghins 1972) and is probably the cost abundant fish leech of catfishes in the :iidwest (Kle:m 1972). Anchor wor:s ('.ernaea spp.) were found on a few specicens of the co=ely shiner, spottail shiner, spotfin shiner, bluntnose minnov, bluegill, and smallmouth bass. .vost of these infected fishes were in poor condition. A slight infection of black stot, caused by metacercariae of digenetic tre=atodes, was obser ted on one. Juvenile creek chub. 1565 063
15 1 & I 2.3 M*"N TO': Tra; et catches have declined since the inception of the progra: in 1974 (Ta51e 2.3-1). The s_.allest yearty catch (822) occarred in 1976 and was roughly h.alf of the 1975 catch (1,610). The decline in the 1976 catch resulted fr== decreat es is the nu=ber of fish taken at the downstrea= stations. The upstrezu catches in 1975 and 1976 were comparable (324 and 295, rest,ec-tively). ~ e nu=ber of sreci= ens per upstrea= collection increased fro = 6.35 in 1975 to 5.19 in 1976. he total number of speci= ens captured in 1974 and' 1975 was i=flated by large collections of juvenile channel catfish do nstress from the ;iacharge. No large collections of channel catfish occurred in 1976. Variatics is the relative abu= dance of so=e species :.ay have resulted fro fluctuati:=s in year class strength. Results of Kendall's coefficient of rank correlati = tests shoved as significant changes (P 2.05) in species ranks at individ:a1 stations during 1974 through 1976 (Table 2.3-2). F1:ct=ations in yearly seine catches resulted fro: large differences in the m:ders of speci= ens taken upstream fro the Discharge (Table 2.3-1). Catch data fro = downstrea= stations were si=ilar throughout the study period. Catches ve e =ost influer4ed by the availability of yoce; of the spottail shiner, s;ctfin shiner, and white sucker /shorthead redhorse. Results of Kendall's coefficient of ra=k correlation tests shoved significant differences (P 2 .05) is species ranks at Stations IA2 (upstrea frc the Discharge) and 9Al (d:rw_s: ea:s fro the ;ischarge) in 1975 and 1976 (Table 2.3-2). 1565 064
16 It is concluded that the i= pact from the operation of Unit 1 on the populations of fishes vulnerable to trapnet and seine was negligible. The ETS requirements for Unit 1 are fulfilled and progra=s will conchaue as specified in the LTS for Unit 2. Bailef, Z.M. , J.E. Fitch, E.S. !!erald, E. A. Lachner, C.C. Lindsey, C.R. P.obins, and W.B. Sco tt. 1970. A list of co:non and scientific na=es of fishes from the United States and Canada. A=er. Fish. Soc. Special Publ. 2. 6. 150 pp.
- Carlandet, K.D. 1953. Itandbook of freshwater fishery biolo:;y with the first supplecent. W=. C . Brown Co . , '.Nbuque, Iowa. 430 pp.
1969. !!andbook of freshwater fishery biology. Vol. 1. Life histery data on freshwater fishes of the United States and Caaada, exclusive of the Percifor=es. Iowa State Univ. Press. Ames , Iowa. 752 pp. Denoncourt, R. F. 1975. Key to the fa=ilies and genera of Pennsylvania fres: water fishes and the species of freshwater fishes of the Suscuchanna River drainage above Conowingo Dam. Proc. Pa. Acad. Sci. 49:32-38. Fowler, d.J. 1940. A list of the fishes recorded from Pecasylvania. Co:z . of Pa. , Bd. Fish Co::2. Bull. 7. 25 pp. Cibb s , R.H. , Jr . 1957 Cyprinid fishes of the subgenus cvsrinella of
'Merette. II. Distribution and variation of lJo3mnis o snilopter's, with tr.6 description of a new subspecies. Lloydia 20(3):186-211.
Hubbs, C.L. and K.F. Lagler. 1964. Fi:hes of the Creat Lakes region Univ. :lich. Press, Ann Arbor, tich. 213 pp. Hugghins, E.J. 1972. Parasites of fishes in South Dakota. Soath Daket.a Dept. Ca=e, Fish, and Parks. Bull. 484. 73 pp. Kle=n, D.J. 1972. The leeches (Annelida:llitudinea) of :11chigan.
- 'ich. Academician IV(4):405-444.
Lloyd, M. , J.H. Zar, and J.R. Karr. 1968. On the calculation of infor-
=ation-theoretical =casures of diversity. A=er. Midl. ::at. 79(2):
257-272. D h ?,)j!qbj\jqr i Va @d@ u 1565 065
17 Miller, J. and r.. Euss. [19637] . The age and growth of the fishes in Pennsylvanie. Pa. Fish Cor:2 26 pp. Pfleiger, W.L. 1975. The fishes of !!issouri. Missouri sept. o f (.cas. 343 pp. Scott , .3. and E.J. Cross =an. 1973. Freshwater fishes of Canada. Fish. Res. Bd. Can. Eull.184. 966 pp. hnelson, F.F. , Jr. 1968. Syste=atics of .the Cyprinid fish ?bercets a-octm, with co=ents on ene subgenus !beroo ts. Copeia 196e (4): 776-802. Sckal, R.R. and F.J. Rohlf. 1973. Introduccion to biostatistics. 2.11. Freeman and Co. San Fransisco, Ca. 368 pp. Sucr.wrfelt, R.C. and C.O. Minckley. 1969. s.spects of tne life historf of the sand shiner, !berosis stramineus (Cope), inethe Smoky i!ill River, Kans..s. Trans. A:s. Fish. Soc. 93(3.':444-453. Treut=an,!!.B. 1957. The fishes of Ohio with illustrated keys. Ohio Stats Univ. Press, Colu= bus, Ohio. 683 pp.
'Jhittaker, R.l!. and C.'J. Fairbanks. 1958. A study of planktor. cepeped co= unities in the Colu .bia Basin, Southeastern '.lashington.
Ecology 39:46-65. 1565 066
j / j >
- ' : w U U \ ,/
Table 2.1-1 Incation of trapact and seine stations. Station Nucber location TRAP!ET UPSTREAM n!- AQ F-1 A3* Off souchwest shore of St. Johns Island. ,
. DWNSTREAM TM-AQF-11A2 TMINS Discharge.
TM-AQF-11A3 200 m downstream from TMI!G Dircharge. n!-AQF-932 1900 m downstreen from TMINS Discharge. SEINE UPSUtEA!! Ut-AQF-1A2 Northwest St. Johns Island. . D!-AQF-16Al 25 m upstream from D1I boat dock. DWNSTREAM TM-AQF-10A2 150 m downstream from TMINS Discharge. TM-AQF-9Al 1500 m downstream from TMINS Discharge. TM-AQ F-933 2000 m downstream from ntINS Discharge.
- Polar coordinate prefix TM-AQF- deleted from station numbers for discussion in text.
1565 067
av D**D W6 oo WI]h$ f budd _, Table 2.1-2 List of corrw. and scientific ru-vs of fishes taken by trapnet a A! seine Juring 1974,1975, and 1976 la the tusquehanna River In the vicinity of 7.!!:3. G-rrun !itre re tentat ac :Me Trapnet .~eins 1971 1'75 _f976 107; to 167-Alewife .slaes -<e. A areneus (.iitson) - - x - - - Ns kellurige M 2-e- mmey Mitchill - - x - - - Coldfish - Car 1** - eratoa (Linnaeus) x - - - - - Carp r -e t- e cs-at) Linnaeus x x x = x x futlips ninnov fv--'- e- avfttf .u1 (Lemucur) * - - - x - x River chub %c~;4 ic m w n tu p., - - - x x x Calden shiner . t ,- - e < c rs eo l ent a s (Mitchill) x x x x x x fer:ely shiner !re :< W e9ua ( Ahl:o t t ) - - - x x x Co-ron shiner - t r a-: < < 'r*urus (::itchill) - - - x x x spottall shiner -t e :4 ' ' a- t s (Clinton) x x x x x x swallowtail shiner rit c-:< er.sne (tope) - - - x x x Kosyface shiner rit r-:< r" ellus (Agassia) - - - - x x Ypotfin shiner trre:< <-ti mterus (Cope) x x x x x v Stuntnose ninnow ri e--iles -otatua (Rafinesque) - x - x x x rathead minnow Pt e-* s t e* rc ei a s Rafinesque - s- - - - - x 51acknose dace Gmte-t s atrat tlus (iter . sun) - - - a x x 1.cngnose dace F 'a - h . t - * * ( staric t ae ('ial enc ier.nes l - - - x x x Creek -hub Fes t: fa aero aculatus (Mitchill) - - - x x x Fallfish S e-v t i s corn ealis (: itc htll) x - - x x x caillbac k Ca"icr#< e e rtnas (Lesueur) x x x x x x White sucker r: rear 2* cc r erwnt (Lacepede) x x x x x x Mrthern bog sucker Ps-a. -te r-- n ier ic aas (Lesueur) - - x x x x Shorthead redborne Ss **c .= rac ele +i e*ui (Lesueur) x x x x x x khite cacfish Ic t ii ;= m (Lienaeus) x x x x - x Yellow bullhead *c til. := natalls (Lesueur) x x x - - x Brown bullhesd Yersh := re5uicaus (Lesueur) x x x x - x Channel catfish Yet t!- :a inctatu (Rafinesque) x x x x x x Stargined e.aJtom vr e- :* t a irnis iRichardson) x x x - - - Rock bass M -it e= -'aestris (Rafinesque1 x x x x x x Redbreast sunfish '.e - fa 1,rttus (l.innaeus) x x x x x x Ptepkinseed ' e- W e c; W' ass (Linnaeus) x x x x x x 51uerill LcN p Jeri chirus Rafinesque x x x x x x Scallenuth bass "f e- -re~s t* *l mieu t Lacepede x x x x x x 1.argenouth bass ' c r--t er s a s tmides (Lac epede) x x x x x x White crapple T m v t s Jamla ris Kafinesque x x x x x x 51ack crappie Pen % : = - t ma c u l a tt:g (Lesueur) x x x x x x ressellated darter !!' era ? a el-*tedi Storer - x - x x x Sans'ed darter F r%
- cr_s Oe.s t e (Cope) - - - x x x Yellow perch Iet ,;,,1 ' ce<ce95 (Mitchill) - -
x - x - Shield #srter ren j a ettsta (stauffer) - - - - - x Valleye Sti--ete.'ien vitreum viere m (Mitchi!1) - - x - - - 1565 068
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32, 725!e 2.2-19
<urTury of fishes taken at trapret station 1M-AQT-113 during 1976.
o..,tw v.i r ;t- En s2 Jul Aue sea orc re t s! Cart h C irp 1 - 1 2 - 1 2 - 7 g,, CilJen shiner - - - - 1 - - - 1 o,3
<r*ttall *litner 6 - 1 - - - - ' -
7 2.4 Linil15ac k - - - - 3 2 - -
$ 1,7 J hite sucker 2 - -
1 - 1 1 - 5 1.7
- rt'iern her sucker 2 1 - - - - - -
3 1.0 harthead re.thorse 1 - - - - - - 1 0.3
-hite catt trh -
1 - - - - 1 - 2 0.7 Yellew bullhead - - - - - - 2 - 2 0.7
- 1. rom bu111 ead 1 2 3 1 4 2 - -
13 4.4 Channel catfish 23 3 4 3 1 10 3 10 62 21.0 "argincJ radtom 1 - 1 - - - - - a 2 0,7 Mvk bass - 7 5 7 - 7 5 6 40 13.6
- RcJbreast sunfish - 3 11 3 1 4 2 -
24 8.1 N pi.inseed 1 15 18 11 11 13 29 Etnegitt - 103 34.9 1 - 1 - - - 2 0.7 White crsprit 2 - - - - - - - 2 0.7
;'aek c ratrie - - - -
1 11 - 12 4.1 litteve - - - - - - 2 - 2 0.7
.' . o n S wn. W 32 4s 23 22 46 o3 16 95
.. of frp. 10 7 9 7 7 9 10 2 19
'i,
- of e 11. 6 4 f. 4 4 4 6 4 36 n 'r a ll . 6.67 8.00 12.00 7.00 5.50 11.50 10.50 4.00 8.19
?i .r*(rv tmfew 2M 2.10 ? . '. A 2. n 2.15 2.48 2 . u. 0.95 2.M 7 5te 2.2-20 urrary of fisl.es taken at tr:pnet station U!-AQF-11A2 during 1976.
.g. 5 nr er mv Jun Jul We "c"
- ic t Total r a ce 'i
% icttunge - - - - - -
1 - 1 0.5 ca r;- - - - - - 1 - - 1 0.5 retlen shiner - - - - 1 2 1 - 4 2.2
-rottail . hine r -
6 - - - - - 1 7 3,3 eret:in whiner - - 6 - - - - - 6 3.2 Mit h bac k - - - - - 1 - - 1 0,5
-ilte <acher - - - - -
2 - - 2 1.1
- arthe.iJ redhorse 1 - -
1 - - - - 2 g,g 3r m bullhead - - - 3 - - . - 3 1.6 channel catfish 3 7 - a 3 7 1 21 46 24.9
.argineJ s dton - - - -
1 - - - 1 0.5 h i bass - 7 2 5 6 1 7 - 2d 15.1 kcJ5rcut sunt ish - 2 4 - - 3 7 - 16 S.6 M piinseed - - 4 7 9 4 4 25 15.1 21ucct11 - - - - 2 2 7 - 11 3,9 val!xuth bass - - - 1 - - - - 1 0.5
*irce uisch bass
. - - - - 1 - - -
1 0.5
.'it te crapple 1 - - -
1 1 1 - 4 2.2 91.h k c rarpit - - - 6 2 6 20 5 1 10.8 c it t. e - - - 1 - 1 - - 2 1.1
'- . at r-n. 5 22 .o 30 24 30 35 23 135
- of irp. 2 a a 10 7 12 9 3 20
'i . et C011. o a a 4 4 4 6 4 36 n..ett. 0.81 5.50 4.00 7.50 6.00 7.50 5.83 5.75 5.14 iv r4 ice ! ,.'e x 1. ' 1.4 1.01 23 2. M 1.M 2 77 ".51 1.35 1565 081
. . _ . . ~ _. _ _ _
33 mn ,-, b' -[l' ] /T T I-][} p , , Table 2.2-21 Sum.ary of fishes taken at trapnet station T'?-ACT-11.0 during 197o.
'%'ath v ar *cr
. 'w
- i:n Jul Aec <cs Cet Totat C a t . '-
Carp - 1 - - 1 - - 4 5.3 Colden shiner - - - - 1 1 - - 2 .7 Spotfin shiner - - - - 1 - - - 1 1.3 Quillback * - - - - - - 1 - 1 1.3 Aire sacker - - 1 1 - - - - 2 2.7 Brewn bulthcad - - - 0 - - - - 2 2.7 ~ Channel catfish 1 2 - 2 - - - 1 6 3.0
?urr.ined maJtom 2 - - 1 1 - - - 4 5.3 Rcck bass 2 1 3 $ 1 - 1 - 13 1 ,)
RrJbreast sunfish 1 1 12 4 1 1 2 -
- 29.3 herkinseed - - 1 - 3 - 7 - 11 14.7
!!uegill 1 - - - 1 - - - 2 2.7 Smallcouth bass - - 1 - - - - - t 1.3 Black cr.1 ante - - - 2 ? - - - 4 5.3 -) . of Spmt. 7 5 1$ 17 13 3 11 1 75 M. of SPp. 5 4 5 7 9 3
- 4 1 14
!b. o f Loll. 6 4 4 a 4 4 6 4 3e n/ coll . 1.17 1.25 4.50 4.05 3.25 0.75 1.83 0.25 0.08 Olversity inlev ?.?? 1.92 1.s? 2.=4 3,n3 1,59 1 ;9 o,og 3,15 Table 2.2-22 Surrury of fishes talen at trapnet station T!!-AQT-932 during 1970 Vnth "ar Apr ?uv Jun Jul Aur fes oc t rots 1 CatSh Alewife - - - - - - 2 - 2 0.7 Carp - - - - 1 - 3 2 6 2.0 siden shiner - - - - 2 - 9 - 11 a.1
- - - - - 1 0.4 Spottait shinar - - 1 Qu111back - - 1 1 1 2 7 - 12 4.5
'"hite
- cat fith 1 - - -
1 - - - 2 0.7 Yellew bullhead - - 2 - - - - - 2 0.' Srown bullhead : 6 1 5 5 1 3 - 23 8.0 Channel catfish 5 7 5 2 9 - 3 4 35 13.1
?brgined ruJtom - - - - - - - 1 1 0.e Rock bass 1 2 4 1 1 - 6 -
15 5.0 Redbreast sunfish - 2 7 - - - - - 9 3.e Pu pkinseed 4 12 31 3 10 4 5 - 72 07.0 Bluegill - - 2 - 1 3 1 1 8 3.0 sma11routh bass 1 - - - - - 1 0.-
'liite - crappie - - 1 -
1 - 12 - 14 5. Black crapple 2 - 5 5 17 5 13 - 47 17.s Yellow perch - - - - 2 1 - - 3 1.1
%*111 cv e 1 - - - - - 1 1 3 1.? !e. of Span. 17 29 5+ 27 52 16 . 63 9 267 W. of Srp. S 5 13 6 13 6 1: 5 19 L. of Coll. 6 4 4 4 4 4 6 4 36 n / Coll . 2.53 7.25 14.75 25 13.00 4.0u 11.33 0.25 7.42 Piverrity indev ?.70 ?.n? .5 2.32 2.93 ?.35 ?: 2.n6 3.32 1565 082
Table 2.2-23 . Sunnary of fishes taken at trapnet stations during }! arch through October 1976. l t gr. If;n - Tlf-A9f*-1 A1 T(1-NLE-11 A 2 Tif-AfLF- I I A3 Tji-69Q'All? Torn 1 7. Catch Alevife - - - 2 ._ 2 0.2 fluskellunge - 1 - - 1 0.1 Carp 7 1 4 6 18 2.2 Colden shiner 1 4 2 11 18 2.2 Spottail shiner 7 7 - 1 15 1.8 Spotfin shiner - 6 1 - 7 0.9 Qu111b4xk 5 1 1 12 19 2.3 bliite 6t.-ker 5 2 2 - 9 1.1 tbrthern hog sucker 3 - - - 3 0.4 Shortheaf redhorse 1 2 - - 3 0.4 bliite cat fish 2 - -
.2 4 0.5 Yellow b :thead 2 - -
2 4 0.5 elrown hu lhead 13 3 2 23 41 5.0 w (.lu.nimt nolIrah (,2 46 6 35 149 Itt .1 ( d_ s ta rr. insiel si.n.li nen 2 1 4 1 !! 1.0 (y son - I.n . .: tw.tbrennt nonflah
'. 0 74 2 11 16 13 22 15 9
9(, 71 11.7 8.6 tM piaapkin9eed 103 28 11 11 2 72 8 214 23 26.0 2.8 Bluegill 2 0.4 EQ 71, Sraa11 mouth bass Largenouth bass 1 1 1 1 3 1 0.1
,3@
[ Uhite crappie 2 4 . 14 20 2.4
~ ~ ~f Black crappie 12 20 4 47 83 10.1
~
! O 20 Yellow perch - - -
3 3 0.4 LJ1 Walleye 2 2 - 3 7 0.9 O M tlo. of Spon. 295 185 75 267 822 LJ1 g !;o . of Spp. tb. of Col 1. 19 36 20 36 14 36 19 36 25 144 CD b DIvorn1'ty in. tex 2.95 3.35 3.14 3.32 3.41 00 U
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j, . . - - . . . . . . . . . . . . A
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2 q.......... . ..--e. - . . . . . .....,e. . l. g ,
. . . . ..... .. ......... . ~.i.... --<
.c ,
13 _..
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.=..e~
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j 4. a, . s
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r , r. .t ..;.. i 3.
, .. e , e ,4 . . , . as
. , , . - .-i .-,. .e...; ... .g.
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. . . 4 4 .; .e <e..r...._..f.'
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r T t g QQ dg.. ,, s 1565 084
36 Table 2.2-23 Indices of percent si=.ilarity of species cc= position between trapnet stations during 1971.,1975, and 1976. 1974 1975
$2.5 ILC 38.7
, 70.3 d5.1 1113 54.2 45.5
" 1. 2
??.' +6.1 c?? 67.1 46.4 63.0, 11A3 ILC LO 1A3 11A2 11A3 49.4 M.3 e6.1 932 62.6 SS.3 ILO 71.2 ILC ,
1.976 D* n
- WWi@
ip w V,4 a' y t[ MdOJg Y 3 Table 2.2 _5 Indices of percent si=ilarity of s;ecies co= position between seine stations during 1974, li!5, and 1976. 1974 %.C IEu 44.7 1975 SS.9 77.0 1&t2 61.0 70.3 71.1 71.3 M.1 911 71.0 37.8 44.4 94 . t. 72.9 63.' M.1 053 56.5 73.3 83.2 f.5.9 9Al 10A2 1EC LO 1A2 16Al 10A2 9Al 79.3 77.9 e7.5 !1.4 913 82.0 7 ?.I. 63.2 9Al 70.5 50.9 10.C 1976 %.4 1E\1 1565 085
37 Table 2.2-27 rishes taae a br seine em 2 ". arch 1976 in the vicinity of -!!:3.
-"- er-tsat v- ' ' -" ,' r - i l er---) -
mat e-- riatt"i -' w r- t A ? i Itcae 1010 1030 1C45 1115 1135 Air 1erp. (C) 6.0 6.0 5.) 6.0 5.0
. ster Te-p. fC) 6.5 6.5 6.5 6.5 6.5 Dissolved (*rygen (ppm) s.8 9.0 9.7 9.3 e.6 PE 8.0 S.! 8.1 8.0 7.9 5ecchi Disc (cm e 51 51 41 36 51 River Stage ffe) 6.20 6.?O 6. t 6 0 4.50
'.*c a r be r roe r.t r, s.e e,
*;.r. . v. ; a. LL le 7 3 -. 81 To. n e ea,. '? h 3 ? A In Co s ty whi .ar -
3 . - - 3 3.- Co_rwn shiner . . . . 1 1 1,2 Spottall shiner . 2 - . 1 3 3.7 Swallowtait shiner .
- 1 - 1 7 9 11.1 sporfin shiner 5 8 5 . 33 51 43.0 Eluntnose minnow 3 - 1 - 1 5 6.2 Blacknose dace - 1 - - . I 1.2 Redbreast sunfish - 1 . .. 1 2 2,5 Tesse11ated darter - - 1 2 . 3 3.;
B.iMed A rter 3 . . . . 3 3-Table 2.2-28 Fishes taken by seine on 15 March 1976 in the vicinity of N:':5 Se at t a -"- w r. t A : - - c c-!M t - " ' -1 - - t r ait -" < - - n -tat < -- Tire 1030 1045 1100 1130 1200 Air Te p. (C) 11.0 12.0 13.0 13.0 11.5 Water ice?. (C) 6.0 5.5 6.0 6.0 6.0 Dissolved oxygen (ppne 10.8 10.8 10.0 9.8 9.5 p!! 7.8 7 ?.6 7.8 7.9 Secchi Oisc (cme 61 61 43 61 64 River Stage (att 5.84 5.54 5.2- 5.94 5.64
's. s t .c r 5
clear (test "teer etese ps-ete e t .5/v Ls. o f V-a. 24 ; f. 3; J1 . 111 x$ af es. 3 s - o Co elv sh aner - 2 . . 2 1.- spottal t *43ner . . 4 1 5 .5 Seallowcait sniner 3 3 2 2 M 10 9.0 E wvfase shiner - . 4 - 4 3.- spotfin s5.tner 15 18 14 26 73 65.2 Stuntnese -innow 6 . e 2 TI5!! 12 10. Fathead cannow . 1 - - 1 0., Redbreast sunfish . - 2 - 2 1.-
' U~ *?
T *
- el ' 1t- f Arter - - . ? 1.-
1565 086
33 Table 2.2-29 Fishes ta'. en by seine on 29 **. arch 19*6 in the vi:1:ity cf n'!x . Stattom T". v r. t G T "- w r . t . , ~ . . . t.s e -e. u' r- u t r- *) - s- : 16mm 1020 1040 IC55 1135 1143 Air Temp. (C) 12.0 12.0 12.0 13.0 13.0
'*ater
- Te :p. (C) 10.5 10.5 13.0 10.5 10.5
. 'ssolved Wygen (ppm) 8.8 9.2 4.7 9.1 '
8.5 pet 7.9 7.9 7.9 7.8 7.8 Seccht Disc (ens 33 41 *1 36 46 River Stage (ft) 5.52 5.52 5.52 5.52 5.52
'e s t6er Overesse th ere s e r --err a s t o crea9t A.e* cast
!.o. o f 5 7=1. 1J 10 h 4 13 ?? -
=:.s . af<-. 1 1 a ? 3 a Spotta11 sinner - 1 ;1 - - .2 ...r Swallowtati s5tner - - 1 - 6 7 ~.3 Spotfin s5tr.or 8 1 13 - 6 2S 7.2 51untnose =ir.now - 4 8 1 e 13 13.5 Blacknose dace 1 - - - - 1 1.2
- Creek chub - - 1 - - 1 1.3 Channel catfish * - - 1 - - 1 1.3 Tessettated darter 4 10 2 3 1 20 02.s traded far e- - - 1 - - 1 '1 D {D su - h6
}_ . . . , . : s p h~ I Table 2.2-30 T!shes takes by seine on 13 April 1976 in the vicisity of n'.1:3 feattea S*- v: r- t u ==.w r. t
- 1 -
-tru -*-nor- q t v. ' r.n i ve 3: ,. .
Time 0922 0935 C%S 1020 1030 Air Teap. (C) 9.5 10.0 10.5 10.0 3t,5
ate r Te sp. (C) - 7.0 8.0 f.0 8.0 1.0 Dissolved Oxygen (ppm) 10.7 10.8 11.0 10.5 10.a PM 7.7 7.6 7.7 7.7 7.7 Seccht Disc (cs) NA 172 137 137 137 River tage (its 4.83 4.33 A.33 4.e3 . 33 t.'e s t 5 e r Pirely rta"fy Partly cie.9 1,- - cloufe pirely etnody Pa rt t s- r ! ae N). of Sp=:s. I e 3) 1 3 3 'h . ef 'aa 1 1 4 1 3 a Spottatt ss.tner - - ;s - ; ;, ,,,,
Swallowtatt shiner - 1 1 - 1 3 ,,3 Rosyf ace shiner 1 - - - - 1 ;,1 Spottin sht er - 4 11 - 2 1; 33,. Stuntnose cu-now - - 2 - - 1 .2 Pxsphinseed - - - 1 . 1 ,,; Tesse11sted 'arter - 1 2 . - 3 ,,3 P W ed far*er - - 1 - . 1 1565 087
39 Table 2.2 31 Fist.es taken ty seine n 3) April 1976 13 the vici:an et T !!!:3.
-" , 3- u 1 !st ' -
gritt-n - - vn - t v -v8-1621 6- t to . ~ ' - ni 1450 1440 1422 1400 1350 Time Air Terp. (c) 20.0 20.5 20.5 19.0 19.0
ater Temp. 'C ) 15.0 15.0 14.0 34.5 14.5 Dissolved 04ygen dype:e 10.0 9.9 9.7 10.6 10.2 pH 7.5 7.5 7.6 7.9 6.0 36 48 61 64 se.sh t Disc (cr e . 61 River itate- f f t. 5.2d 5.*t 5.28 5.23 5.28 *. .. s the- r1ese r1e ar riear o c1ese r1 ear
- No. of spr.n. 17 2 ;* ' 1 ) .s 1
?;a n' e-=. 3 ? 5 1 spottant shiner
- - A le.3 Swall atait shiner 7 - 1 30 61.2 Spotfin shiner 6 1 19 1 3 Bluntnote minncre - - 1
- - 1 2.J
- - 1 2. ,
sr.all-outh bass - - 1
- - -
- l'.-
Te==citat-1 este+- a 1 e. Table 2.2 32 Fishes taken by sel .e on 10 ay 1975 13 the vici:I n of T3!;5
. ... - . ..t. ., .pn ~. ;< r. c 1 -* r -3 i. ra-sg3e..,
1035 1015 1000 0962 C930 Tine Air 7erp. ac) 22.0 $3.0 20.0 19.0 !!.0
- ate? Te p. (C) 16.5 19.0 16.0 15.5 16.C DissolveJ bygen inm 8.7 9.2 8.4 9.1 5.6 pH 7.9 7.9 7.9 7.9 8.0 107 107 107 107 Secchi Disc (c s 107 River State (ft) 4.51 . 51 e.51 4.51 4.51
* ** Mt' er
. r1v1r (1*se (1 car ricsr r1*ar
- b. of spe.n. L
- 2
. ?
':n . ne e-n. 1 - 2 .
JJ.;
- L i Blungnase P.tenc e
,r... n' risH Tue := risH rm: ,
1,..cu ,t,4 1 i om m mr a D D D n
'iu i }
A u Table 2.2-33 gg j [, , Fishes taken 1 r seine on 24 ay 1576 in the vie. in of T*t!!;S.
~..r. , -. .*- - '. p i . t . - - .;nc.wg1 -~.so .ogy -Tal at
.;g3.;,q .
Tirae 1040 1025 1005 0943 0927 Air Te 9 (C) 16.5 16.0 15.0 15.0 15.0 1.*ater 7eep. (C) 16.5 16.0 15.5 15.5 16.0 Dissolved oxyges 4;p=t !a !a !A !a a pH 7.5 7.5 7.5 7.5 7.7 Seccht Disc (c:s 33 41 41 51 56 River stage <fts 5.5) 5.:) 5.83 5.6) 5.83
'.c s t* e r c' car e'er- riese ricar ricar 4 - J; .)
?.o. o,af : r .n. J .
- s -
', ca,. ? ! .
- - 3 1 . .s Spottatt shaner swallovtsit shi ar 1 - - 20 - 1 2.2 Spotlin shiner 1 - - - ! 2.2
- . FISH & a 6.,
Creek chuo -
- 30 30 t6.7
'htte sucker /Shorthead redhorse -
Smallrouth bass 1 1 1 tac?; 1 - 6.s
* ?.-
- - 1 Tessellated dar a- -
!a = :.vt Ava.la:.e 1565 088
40
**ie
.. 2.?-34 1shes taken by seine on 7 June 1976 in the vietatty of nt!?:3.
's T. t s! r'*
terio9 " * - O r-t \? -"- WF-18+nt -
*v'5-10\? 1" -4\1 "*- - 9 F = w = 1 'ime 1040 1030 1010 0945 0930 .tr Te p. (C) 22.5 22.0 22.5 21.5 21.5 19.0 e 19,o 19,5 later Tew. (C) 19.5 19.5 .
61ssolved oxyges (pps) 8.2 7.9 8.7 7.9 8.2 in 8.2 8.1 7.9 8.0 8.1 seccht Disc (cm) 61 $6 51 56 61 Li er f*?ie (ft) 4.49 4.69 4.69 4.69 a.69
.ert,,r rsesr ele ir c 1. s - *f n clesr is. o t 5 ptsa. if 6s3 21* 333 5 ; 's .192
- c. af ea*.
- a 9 A 4 11 spotta t t ciner je an ;; 249 773 taa) u..
ivallovtatt shiner 2 - - - - 2 ..: . ipotfin shiner 26 8 6 - - 40 *1 . 4 = . 4 c.; Stuntnose minnov - - antnose dace 1 - 2 - 7 to i. 5 .
- reek chub - - 1 4 12 17 C.t Alte sucker /Shorchead redhorse 8 324 123 85 84 624 2t.'
tedbreast sunfish - - 2 - - 2 4.1
- 1 1 81uesi11 - -
ressellated darter 5 - 3 1 - 9 C-thield dirter 1 1L 1 ? - 19 '.'
+ = less tham 0.05*.-
D*G RWricnnon , jit t Il ]jfsaj c \\ ., joi
. u b' ' u. c dfla Table 2.2-35 Fishes taken by seine on 21 Jane 1976 in the vicinity of T*tt ;5.
T"-to--Ic\ n m r-+\1 -"- ir-was r. . r a t -
**att m -- o -it? ' -u'6.t*\1 1030 1015 1000 0932 0920 T ic.e Air T6sp. (C) 25.5 26.0 25.0 24.5 24.5 Water Temp. (C ) 25.0 24.0 25.0 25.0 25.0 Diss.31eed oxygen (ppm) 7.8 6.4 7.0 6.5 6.1 pH 8.7 8.1 8.3 8.5 8.2 30 30 30 30 30 Seccht Disc (cm)
River Stage (ft) 4.42 4.42 4.42 4.42 4.42 A.creage We s t be r N ereage n eresse A.e ease M ereigt 3,1 kb 403 av 230 1419
- 42 of s peri.
6 e1 7 4 5 I? vo. of <ce.
- 3 1
- - 4 c.;
Conely shiner Spottall shiner 371 261 372 77 193 1274 !i.t Spotfin shiner 2 8 6 5 8 29 2.
- - - - 1 c.;
81acknose dace 1
- 1 - - - I c.*
Lonanose dace 24 1.7
- 2 8 2 12 C ree k s tu.b 6htte sucker - 1 1 - - 2 0.*
16 - - - 16 !.* Shorthead redhorse - 2.5 10 3 16 33 6 tite sucker /Short5ead redhorse 4 -
- - - 1 .;
pu pktoseed 1
- - 1 - 2 C.:
Smat temmth bass 1 11 1 1 30 :.. Tessellated earter 12 5
- - - 2 c h i , t .4 dirter - 7 1565 089
Table 2.2 36 N Fishes taken bf seine on 7 July l's76 in the vicinity of T:tt:3.
"= u '* '"- 'a4:2 ~- r '* "- * *3 *^t1' IT-
*"-e -1:'
Steeton 0935 1020 1000 1115 1130 Time Air Temp. (C) 22.0 21.5 21.5 22.5 24.0 k*ater Te- p. (C l 24.0 21.5 24.5 24.5 25.0 6.6 7.0 6.y DissolveJ Onyten (pprs) 6.8 6.2 7.3 7.6 7.3 7.3 7.2 pH
- 36 30 30 33 TJ Seccht Disc fc=) .46 P.1ver Stage (ft) 4.;6 4.;6 4.48, 4.16
^ +rraet we-cast ^ ereast 'e-- a.* N ereast WestNr 6)s e.) 1:Y s )$1 le,=
S. of SPnn. 9 7 e t-
%. af c-w. ? 19 *
- - . ;j ..
Cumely shiner - 23
- - - - 1 ..
Co-run shiner 1 61 2 r,0 1361 ti.. 515 355 150 SPottatt shlaer 1 1 . 36 2.! 3 Spotfin shiner Rtuntnsse otn.w 31
- 2 1 3 .:
- - - 1 .
31acknose dace 1 16 !..
- 1 4 8 3
-Ta11 fish , 6 131 145 t.f
- 8
*htte
- sucker -
- - - 1 ..!
- 1
!brthern hog sucker
- - - - 1 1 .1 Shorthead rednarse - - 16 !.-
10 6
*'hite sucker'Shorthead redhorse -
- - - 4 4 2 Brown bu115eaJ - 7 12 *7 .
- 5 Channel catfish -
- - - - 1 *1.
Rock bass 1 24 .a 5 9 2 3 5 Smallmouth bass - - 3 ..
- - 3 -1.!te crappie 2 1 2 7 8 29 17 Tesse11sted darter * - - - ? *s~'ed /sr ce A
(pi epj .il> IV Table 2.2-37 D j , . a Fishes taken by seine on 19 .41y 1976 in t. e vici-ity of T".!:;5. h I!I"" t"d id k< i a i.
' rr-; 2 <r--! -o-. - .i t c e , e n., -....a-t .< r - ?
- u -
1446 1355 1331 1398 1253 Time 24.5 *1.0 25.5 27.5 27.0 Air Tenn. (C) 2;.5 24.5 water Terp. (c) 25.0 21.0 24.5 Dissolved Nyten (rpm) *a. 7.2 7.4 7.- 7.2 7.8 7.8 *.s 7.7 7.6 pH 30 23 :S 29 30 Seccht Disc (cn) 4.51 a.51 River Staae if t) 4.51 a.51 4.51 Veerb r riese c'e*r r'es* c'ei- ricar
. ri. 124 JJ J> 079 50 of tren. 2:s e
- St 14 1' In
%3 of c 9 . - g ,,,
- - 1 Carp - - 9 g,3 4 3 2 Co ely shiner - - - 6 *.)
Joerion shiner 4 2 Spottall shiner 218 l'S 83 52 1: 493 7;., 47 3 : 3 - 55 t.1 Spotfin shiner c,-
- - 2 1 3 51untnose ninnov 2
- - - - 1 ;,1 81acknose dace 1
- - - t .:
- 1 Creek chab . 1 - , a ratifish
- 3
- - - 1 ,;
- 1 Quillbac k 2 6 5 20 ..r white sucker a 3 a ; 3a t.y 6 23 shorthead re horse 1
- - - - 3 3 ,,.
Brown bullhe J - . - 1 ;
- 1 Rock bass - - 1 - t ,;
ReJbreast sanfish - - - - g , Punskins eed 1 1 1 1 ,,; 6 3 3 5.a11ooota ta s - - - 1 ,;
!.argewth bass - 1
- - 1 ;
- 1 Ehite cra n te -
9 6 3 6 24 2.5 Tesse11ated darter - - t
!snded dirrer - ! -
1565 090
42 Table .* 38 T1also taiss ty seine en 2 A. gust 1976 in the vistnity of T!*!!3. eest!-- N-ace =142 m-Arr.1 tat "* AC F- I C A 2 ~'*-
- f, r . e g t tu. of r. " ) T'til i 2 t c P-Time 1005 1C28 1042 Ilta 11?2 A r Te 7. (C) 20.0 19.5 0.5 20.0 20.5
-'ater e=s. (C) 21.0 21.0 21.0 21.0 21.0
- 1s ulted W 7ses (ppm) 8.0 7.8 6.2 8.0 7.9
- 3 8.5 8.4 8.1 8.1 8.0
.4cchi :isc tes) , 30 33 33 33 30 Eiver s. ate tit) 3.96 3.96 3.M 3.96 3.9 .e**'e- Ptrtly Floudy htt!v rte W Portly r!wdv Frtly.8toudy Partly etoudv
- 2. 3. m.,==. - el , J.- ) e3 J $1 271 $N
.. .3 s. 7 4 A 4 7 1A G e.v s .1.er 1 - - - - 1 0.2 G m shi er 5 3 - - - 8 1.4 fretta11 shi er 19 97 35 29 8 187 32.5 fperfis shimer 1 - - - - 1 0.2 11 z use si..now - 7 2 3 - 12 2.1 Fa;1f t.sh 1 2 - - - 3 0.5
'?. ire suchar 1 2 4 1 8 1.4 ertlers bog suc*er a - - - 1 ,- 1 0.2 nsruest reshorse - 4 6 4 - 14 2.5 Tel re N11 head - - -- - 2 2 0.4 Ir:vs hil'.ead - - - - 2 2 0.0 U.a-me! catfish - - - 3 256 259 45.4 3ersteast essfish - 1 - - - 1 0.2 5 cal" r::th bass 2 1 7 1 - 11 1.9 0.2
- .te crante - - - - 1 1 e s s. :sted forter to 9 13 17 1 11 10.5 Q
@ 9 Tip p ' I rr O
Tatte 2.*-37 " ' d2 Tistes takes by seine on 16 August 1976 in the vicinity of TM!!3. rearim r-;4r-t\2 re-Atr-l'At -~. o r.1 m 2 ~. . ant ?!t- A0 r. 9 p y3t c3c-r Tine 1f45 1000 0945 C920 0905 Air Te 7 'C ) 18.5 15.5 18.s 18.0 18.0 ater Te=p. (C s 19.5 20.0 20.0 19.5 20.0
- isolves eryges (ppm) 7.4 7.2 7.3 7.5 7.8
-4 8.0 8.2 8.0 8.3 8.4 5ecchi risc test 25 28 28 28 28 tirer 5tage tit) 4.52 4.52 4.52 4.52 4.52
.ent'er riesr etear fleer -! ar tiear
."o. :1 !;==n 32 126 108 al 104 419 "c . -f N . 4 12 to !? 9 19 tiver ct.s 1 -
1 - - 2 0.5 ms!v shtaer 2 2 - - 1 5 1.2
- -rm shiner 3 6 - - 1 10 2.4
!pettati shiner 5 71 64 20 11 171 40.8 i<all.v.all shir.er 2 - - - - 2 0.5 Ip:sfLs shiser 12 23 3 5 12 55 13.1 Ilu:tzse 31 snow 5 3 1 1 23 33 7.9 Ta;1fis h - - 1 1 - 2 0.5 ?.!!, nceer - - 1 - - 1 0.2 Ibrt .ead ce4hcese - 2 6 4 - 12 2.9 lu a tass - 4 - - - 4 1.0 tedireast svatish = * - 1 - 1 0.2 P_P iaseed - - 1 - - 1 0.2 1*.e-ill -
1 - - 3 0.7
.alin..th bass -
2 4 1 2 9 2.1
. .ite e rante - 1 - 4 18 23 5.5 !!aca crante 1 1 - - -
2 0.5
* *. et t st ed f a rter t R 26 ** M 63 to,e 1565 091
43 7able .7.2-40 rishes taltes Sy sete.e es ! Yett-eter 19'6 is tr.e vicinity of S1:;3.
- -v -t e "- a-141 -"-u."-l u2 ~"- e -
- u ~ ' ' , ' --is Totat r ate-Stat *-,
1358 1355 1 13 1445 15C0
** 1 =e Atr Te p. (C ) 24.0 26.0 25.5 26.5 25.5 22.0 22.5 22.5 23.0 22.5 * *at er ie-7. (C )
7.7 8.0 Disssived Osygen rme 8.3 8.1 7.o pH 5.5 8.5 6.4 8.5 8.5 33 2* 29 39 30
' . chi !!*c (enn S.73 3.73 3.73 3.73 3.73 R!ver
,3ei .'tage (ft.* . . . . , e p. . e ..ety ro w . 3.-. s. - % = 1y r f ;
- hre. et-J.9 11- .- es 621 M. : >,ta.
4 M
- m. -- % . i a t? 11 7 Cut!!;w rinnow - - 1 - - 1 6.2 1 - - 1 C.2 River chub - -
- - - 1 0.2 Coldes shiner - 1 Corely shiner - 1 2 - - 3 0.5
- 7 - - - 7 1.1 Co-xzn shiner .
Spotta11 shiner 13 1 01 24 12 3 156 25.1
- 8 - - - - 8 1.3 Swallowtati shiner 172 16 4 33 - 225 36.2 Spotfla shiner 4 3 - 10 1.6 slu=tnose nianov 1 2
- 1 0.2 Creek chub - 1
- 4 1 1 - 6 1.0
*. tite sucker 2rtt.ern ho, sucker 2 - - - - 2 0.3
- 1 3 - 6 1.0 Shorthead reds.orse 2
- - 1 0.2 htte catfish - - 1 56 28 41 127 20.5 cha=nel cattish - -
- - - 1 0.2 Pe :psinseeJ - 1 Bluegill - - - - ! ! 0.2
- - - 4 0.6 5=all outh bass 1 3
- 4 C.6 Black crappie - 4 - -
regge11Seco 33rter ?! to 7 14 s SA o.t 0 f l 0 Table 2.2-41
! ,; ' I'-( ( 1, f.V a b b ;~t' a a $U0 s 3
rishes taken by seize :: 13 !epte ter 1976 in the vicinity of n'.155.
~-aff-1A' "-\^r-!*nt N. '
-t r a w.m r- .11 -.<6.q, -. a t rt --
Ara Pn Time 1432 1345 13 6 1253 1:40 Air Teco. (C) 27.5 28.5 :6.0 26.0 25.0
.*ater Te p. (C i 21.5 21.5 21.0 22.0 2.5
*Jissolved Oxygen ( m ) 7.6 7.7 7.5 7.6 7.8 pH 8.5 8.4 8.4 8.6 8.7 36 46 33 53 53 Seccht *)1sc (es)
River Stage (ft) 3.43 3.48 3.48 3.48 3.48 etear etear ricar ri ca r riaar i Lest'er 114 54 H 21 77 325 M. et SP n. % 1:
%. of (*p. 4 to 4 5 8 1 1
- - 10 3.1 C::aly shiner
- - - 1 0.3 Cc-ren shiner - 1
- 65 la 0 Spettati shiner 16 26 18 5 49 - 19 - 1 69 Spot!!n shiner 3 3 - - 19 ;
Bir. tnose esinnov 13 0.6
- - - 2 Shrthead redhorse - 2 7 72 69 27.e 8
Chanset catfish 1 1
- - - - 1 0.3 Roc',eass 1
- 1 - 2 G.9 Fe Preast sar. fish - 1 1
- - - - 1 0.)
Pu pninseed Blueg111 - 1 - - 1 2 0.$
- 2 - 3 C.9 Snaltecuth bass 1 -
17 to 6 2 60 13.5 Tessettated .larter 25
- - - - 1 n.?
1 manded darter 1565 092
44 Table 2.2-62 Fishes taken by seine on 29 Septe-ber 1976 's the vicinity of TMIN3. ftstion a.. w r. t u * ?-e -16 1 N >~4f.* 1dA ? -"* ** M ~~ #~"3 I"f3I #d* Ties 1330 1415 1433 1E6 1520 Air Ter p. (C) 19.5 20.0 19.5 19.5 200 Vater Tc p. (C) 16.0 17.5 16.5 17.0 17.5 Dissolved Oxygen (pre.) 9.6 10.1 9.8 9.9 10.0 pH 8.3 8.2 S.1 4.1 9.1 weht Disc '-mi 30 30 30 36 il River Stage (st 3.85 3.65 3.65 3.t5 3.es Wither Pertty r ta My Pietly < !c Mv ?artly etnuJv P i - e efy ra r* 1 r c lou.h-M. of sp-:n, 339 27 ;31 -, 2.; 11ve
%t of Sa . 7 4 !! ! e 15 Corely snir.ar 1 - - - -
1 0.1 SpottaLL shiner 3 9 8 12 -
- 32 2.9 Swallevtati shiner 2 - 1 - - 3 0.3 Spott!n shiner . 510 - 173 -
221 909 82.3 Stuntnose ninrww 2 1 10 6 - 19 1.7 Creek chub - 1 - - - 1 0.1 Fallfish. - - 2 - - 2 0.2 shorthead rechorse - - 1 - 1 2 C.2 Channel catfish - 1 & 2 1 8 0.7 Redbreast sunf tsh - - 1 - - 1 0.1 Pumpkinseed - - - - 1 1 0.1 Bluest 11 - - 1 - - 1 0.1 smallmouth bass - - 1 1 1 3 0.3 Tesse11ated 6..rter 11 14 44 19 22 110 10.0
?amfed dirter to 1 - - - 11 1.c
.r;,
n
> l } T'G G jil l9 '
. Ijh 0 I jl\ {wn{dbudt' o Table 2.2-43 Tishes taken by seine on 19 October 1976 in the vietnitv of TMINS.
Staeton - -i.n e. t A 2 *- r- t ' ; t -"- 4 0 F- 10 A ? - ' - : ast -"- ;'4- 3 3 Torag e3te, Time 1518 1637 1618 1147 1328 Air Teep. (C) 12.0 12.0 12.5 12.0 13.0 Water Temp. (C) 11.5 11.0 11.5 11.0 11.0 Dissolved oxygen (ppa) 12.4 12.7 12.7 12.5 12.4 pH 8.1 4.1 8.1 8.1 6.2 Seccht Dise (cm) 30 33 36 48 46 River Stage (ft) 5.34 5.34 5.34 5.34 5.34
*. 'e s t % *r rieer Part!v r!audy clear ft-ar ivrtly Cloudy _ '.o. of Spmn. 4') 7s 265 a W 506 *$ s f t a3. 4 '. 9 6 e 1 Corely shtr.er 1 - - -
- 1 0.2 Co:run shiner - 2 - - -
2 0.4 spottatt shiner 6 21 22 3 - 52 10.3 Swallowtail shiner 2 2 10 - 5 19 3.8 Itosyf ace shiner - 1 - - - 1 f'. 2 spotfin shiner 6 3 181 1 57 248 49.0 Stuntnose minnow 11 13 18 - 3 45 8.) Fathead minnow - - 1 - - 1 0.2 Fallfish - - 1 - - 1 0.2 Rock bass - - - 1 - 1 0.2 Purpkinseed - - - 1 - 1 0.2 Snattreuth bass - 2 - 1 - 3 0.5 Tesse11ated darter 23 31 31 17 25 127 25.1
*gnaea daree- - 1 1 - - o9 1565 093
t.5 able 2 2*'O etshes ta)en bY seine on ;5 occe;,vr g 93 g. g:.e vicinity of D'3*
.a t un .....,e. , ,3 .
..ar. w ,,,,,,,.g . ,
- 1. . s e ,,,
W 0935 I0I gg39 110s, .g;; air Temp. ICI v.0 **$ 9.5 $ ; ,,e, dater Te*7. (C)
- 7.5 I*I Ro 7 7.5
.tego)ygd Dxygem 'PP 8 12.6 12.5 12.6 12'I7 **$ ;4 g5 8.5 ,,3 ,. h4 ,g
- eccl.1 s!" 'C"' I 14 g 1) ;,
yty,r Stage (It) 7. 9a I*94 7, % s.,*%er I*S* r,,, 'e r ne
- a. o n W 17e
*I g 91 m Sil ,, e r ~,- 10 '* y b 4 11 cc.ety sniner 2 s 2 ,
C a n ehl"*F g * . - . 1 C'* spottatt shiner 25 47 g5 31 4 12 Ws11ovtall shiner g 2 5 0 2 2I 2M
~~'
bsytace shiner 3 , . e . S *** cpt fin ah!" 322 3 M 20 '
*2 205 .t*1 21untno** Ell"*
- 1 3 2
- 2 6 ',
15 w itibach . * .
- g 1 C**
Redtreast sunfish . I % . I . 2 m kinseed . 1 . * . 1 0, M uuttil 1 * , . . C*; 1 C Izaltnough bass I I 2 * , f, 0 .-
' *5 e,4,,.}}pte4 darteY g 9
- 7 33 5* '
I
\ +
1565 094
Table 2.2-45 46 Succarv of fishes tai a at seine station l'!-AQF-1A2 durin.; 177s. t ' t's mr apr mv . fun v s .- .* .s t e i: e at River shub - - - - - 1 - - 1 - Ce=ely shiner - a 3 4 3 14 0.7 cc-vun shiner - - - - 5 s - 1 1- 0.5 S70ttail shiner - - - LOT e13 24 3.- 11 13e7 a?.- Sval10wcall shiner a 7 4 2 - 2 10 to 3, 1.4 Rosyface shiner - 1 - - - -
- 2 3 C.1
$rotfin shiner 2S 6 1 28 7$ 13 N1 138 la23 33.7 31untnos e minne. 9 - - -
2 5 le 12 -- 1.7 31acinase daea 1 - - - 2 - - - 3 0.1 la p se Jace - - - 1 - - - - 1 - Fa11 fish - - - - - 1 - - 1 -
~*aite sucker - - - - 4 - - - - 0.2 !br*hern hog sucker - - - - - -
2 - 2 0.1 Shorthead redhorse - - - - 1 - 2 - 3 0.1 White sucier/ShortheaJ reJhorse - - - 12 - - - - 12 0.3 Channel catfish - - - - - - 1 - t + Reek bass - - - - 1 - 1
- 2 C.1 Pu=pkins eed - - -
Bluegill - - 1 1 - - - 2 0.1 1 1 5:211eruth bass - - 1 1 11 2 2 1 18 0.7 Slack crappie - - - - - 1 - -
- 1 Tesse11ated darter a a ! 17 2 20 57 '
s 133 5.0 SanJed da-ter 3 - - - - -
!? -
13 0.5 4hteff darte* - - - 1 - - - - I - 15 of 57 n. 44 18 - ui0 92- 60 373 ' 7 loai M. of 3pp. 6 4 4 9 12 11 12 to 25 W. of Coll. 3 2 2 2 2 2 3 2 15 n /C.11 16.33 9.00 2.03 235.00 4e2.00 113.50 Pfvereity Infew 40.00 291. 1*e.9a 1.5' t 77 ) 0.*a ^.'; '.71 1. 5 ? -? !
- = l e s s t ha:t 0 05'.
~
Table 2.2-46 D 9 71 3 ?.Es. 9 f Y s Su rary of fishes taken at seine station I-AQF-16Al during 1976. J .3 w-t =a r A,- s- An A.x .- Wr ti rat - Golden shiner - - - - - - Cc=ely shiner 5 - - 3 26 2 40 Co rra shiner - - - - 2 2 1.3 2 9 3 2 21 0.) Spottall shiner 3 - 600 ;S3 168 ID 03 14o1 6.4 Swallowtail shiner 4 1 - - - - - 4 9 0.a Rosyface shiner * - - - - a a Spotfin shiner 0.2 27 5 - 16 6 23 16 6 9+ .- Bluntnose erinnow a - - - 2 10 e 16 Fathead =innov - 35 1.7 1 - - - - - - 1 - 31ac cose dace 1 - - 1 - - - - 0 0.1 Lor 4:ose dace - - - 1 - - - - 1 - Creek chub - - - 2 - 2 e Ta11 fish - - 0.2
- - 4 2 - -
6 0.3 Quillback - - - - 1 - - - 1 -
'- tite sucker - - -
1 3 1 e - 9 0.4 krthern hog sacker - - - - 1 - - - - 1 Shorthead redhorse - - - 16 o 6 2 - 30 1.3 White sucker /Shorthead redhorse - - - 324 10 - - - 334 14.7 Channel catfish - - - - - - 2 - 2 0.1 Rock bass - - - - 4 Redbreast sunfish - 1 - - 5 0.2 1 - - - Purpkinneed - - - - - 1 1 1 4 0.2 Bluegill - - - - 1 1 2 0.1 Smallenuth bass 1 1 - 2 0.1 Largecouch bass 1 l' 3 3 3 *: 1.0 1 - - - 1 - rhite crappie - - - - - 1 - - t + Slack crappia - - - - - s Tesse11ated darter 10 1 - 5 0.2 2 - 11 IS 17 41 40 139 6.1 Banded career - - - - 3 fhie!! isreer 2 3 S 0.4
- - - 16 - - - -
14 n.7
- 2. o f sp .rt. $6 8 1 991 379 249 2J5 15 0 2209 M. of 3pp. 9 3 1 10 15 15 17 12 29 No. of Coll. 3 2 2 2 2 2 3 2 16 n/ Coll 18.67 4.00 0.50 495.50 237.50 120.50 73.33 75.00 126.00 r i , e-= i t s- YMew ?.M 1.?O -
'M
'!e 1.on 2.1- 2.32 1*
+ = less than 0.05i 1565 095
47 D
~
TD O' 0 ' R ,Q
- at. .2.u MJ ENd$jlb'b]'
-: mrv i f f hhes taken at seine station *' AQT-10A2 during 1976. % ,t * "ar w ".vr 'an 21 Au (e, qr a n' "sts' earp - - . - g - - - g g,;
euttips r.tnnew - . - - - - 1 - g c,g River thub - - - - - 1 1 - 2 0.1 c.c=1v shiner
- 1 2 -
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. all wtail thiner 3 2 - - -
,- 1 15 21 1.1 4 - -
' U $'-f s. e *h iner - - - - . f, o,; v tiir. *Siner 30 r. - 12 3 3 201 Oc<, 4n 0;,5
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1 10 3 1 - 15 0.5 W rthraJ redhorse - - - - 23 12 0 - 37 1.9
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- eusker/ hortheaJ redhorse - - - 133 6 -
- 13) 7.0 Uhite *atfish - - - - - -
1 - 1 0.1 t ha.-nel c at f ish 1 - - .- 5 - 70 - 76 3.5 LeJbrea t sunfish 2 - - 2 - - 1 - 5 0.J M kinseed - - - - - 1 - - 1 0.1 Elvecill - - - - - - 1 - 1 0.!
.311muth bass -
1 1 - 5 11 1 2 21 1.1 "htte crapple - * * - 1 - - - 1 0.1
.'es.c11arcJ darter 5 2 1 8 5 39 61 35 16: e.
?a.1Jed Jartcr 3 1 - - - - - 1 5 0.3
- 51. ! ? hrter - - -
1 - - - - t r.1 _ ri . c t .p.n. 34 el e e22 393 173 ela 332 -00
- k. ot frp. 10 4 11 13 10 16 10 25 ri. of sell. 3 0 2 2 2 2 2 2 16 n ?co ll . 29.67 30.50 3.00 311.00 151.54 ff.50 138.00 166.00 111.11
~tve-elev ?, Jew ?.18 1.77 1.79 1.?? 1.14 1.40 2.20 1.'3 ? 15 Tat le 2.2-48 su-rurv of fishes taken at seine station P'-AQT-0A1 dt.fint 1976.
V-t': "a r W 'd v 'u n 'ul e- pen Nt Teral c a t e. (.Tely shiner - - - - - - 2 e.; f rctrail shiner 1 - 317 113 'S 29 34 54: 53.4 s-allowtait shiner 3 - 2 - e Spotfin shiner 7 0.7 26 1 5 a 5 33 21 95 9.a Bluntnose minnow 3 - - 2 4 9 - 18 1.9 Creek enub - - 6 - - - - o 0.6 Ta11 fish - - - 9 1 - - to 1,0
'"htte - suc ker - - - 12 4 1 - 1; 1.;
Vrthern hog sucker - - TISH - - 1 - - 1 u,1 ShortheaJ redhorse - - - 4 3 3 - 15 1.5
'."hite sucker /Shorthead redhorre - -
88 - - - - SS 6.7 Channel catfish - - - - 3 37 - !.0 e.0 Rock bass - - - - - - 1 1 0.1 ReJtreast sunfish - - - 1 1 1 1 4 0.4 N .pilnseed - 1 TA C - - - - 1 2 0.2 31uetill - - - 1 2 - - 3 0.3 5 all-much bass - - 1 4 2 3 1 11 1.1 Alte crappie - - - 3 a - - 7 0.7 Tessellated darter 5 - 2 10 29 39 50 135 13.a 5%teld Jarter - -
? - - - -
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M. ot 8r n. Je : - 422 te2 112 155 115 1000
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!b. of Coll. 3 2 2 2 2 2 3 2 is n/ Coll. 12.67 1.00 - 211.00 St.00 Se.C0 51.67 57.50 53.59 fvarete fraev 1.14 1.c0 -
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- 5. rarv of flees takes at == ine .t at 1 n .* sr a nz L rs h t' raue . tc's r i #7e.
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2-alJes shiner - 1 - - - 1 . e.- elv *Siner 1* ;9 li 2 1 7e t.' !.*==rin shiner 1. ?! - - 2 17 n,. f rettail shiser 1307 l '.e t pt s 5 '.2 12 e3 552s $2.* J-allastait shiner 3s 9 .1 7 21 n .. Rasyface shiner 3 - - * - f petits on t. r tf23 49 ;? - vi 1*1 2072 1 -a . -
!!ustasse r.inem 1 ;9 .* 1% .e 1+2 L.
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'5tte sucker a 9 15 17 Il? 182 1.*
'i et! ern hog suc ker 1 - 1 - - - i orthead recharse 1 30 37 15 . no o.3 -Site sucher/shorthead reoorse 12 33; 13) eg 130 *u) *; . -hire catfish - - 1 - - 1 - Teltow bulthead - - - - 2 2 - 3rewn l'ulthead = - - - 9 9 0.I Channet catfish ! 2 7e 40 377 ;9e .7 Rsch bass 2 5 - 1 - 6 C. i e(Steest sunfish = . 5 ; 1 1; 0.1 P.- phieseed 2 2 L 2 2 9 4.* !!sesilt 1 2 L 3 2 9 a. . ' $ :all9outh bass 18 22 2' 11 10 s2 0.P targe rough bass - 1 - - - t = =%ite craopse - 1 1 7 19 Os 9.3 ?!ack crappie 1 5 - - - 6 0.1 Tessettsted darter 133 139 162 135 109 47A e.5 !acJed darter 13 8 5 - - Je 0.2 Siet_* dirter 1 16 1 2 - 6 - 'a. o f S pr.a. OtM 2269 . v) 1U06 25%s 60 :n \>. of 5pp. 23 29 25 19 21 3) No. of Coll. 16 18 1s 18 is 90 s' Coll. 1&o.3a 126.04 111.11 $5.8 9 102.!! 11 6.'. 2
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) d Table 2.3-1 Sumar/ of number of speci= ens, nu=ber of species, - 'er of collections, and number per collection of fishes taken by trapnet and seine upstream and downstrea:
from the T:!I:? Discharge during 1974 through 1976.
- u=ber o f !!u=ber of ?
- ::ber of !; umber per Seeei= ens coecies r:11ections Collection TRAP .TT 1974 713 19 36 *19.81
, Upstream 1975 324 20 51 6.35 1976 295 19 36 8.19
, 1974 1257 20 72 17.46 Downstream 1975 1286 21 87 14.78 1976 527 24 108 4.8S 1974 1970 22 108 18.24 Total 1975 1610 22 138 11.67 1976 822 25 144 5.71 S EI!.T 1974 3460 24 28 123.57 Upstream 1975 1558 24 30 51.93 1976 4914 30 36 136.50 1974 5127 28 45 113.93 aownstream 1975 5016 29 45 111.47 1976 5564 31 54 103.04 1974 8587 30 73 117.63 Total 1975 6574 30 75 87.65 1976 10478 35 90 116.42 1565 132
84 D n -. lle Il}N?UDf bOk(llfffI Table 2.3-2 Kendall-tau correlation coefficients for species composition at trapnet and seine stations during 1974-1975, 1974-1976, and 1975-1976. 19~7?.- 19 7 5 1975-197- 1975-1976 T?.A??.~ET 1A3 0.65 0.47 0.47 11A2 0.69 0.59 0.70 11A3 0.59 0.35 0.48 932 0.62 0.57 , 0.51 SE!NE , 1A2 0.55 0.40 0.22* 16Al 0.60 0.42 0.44 10A2 0.57 0.25 0.26 9Al 0.37 0.34 0.26* 933 0.61 0.52 0.37
- Significant at 957. level.
1565 133 I
85 _ FALL J HILL Is12;a
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4 TM-AQF-932 SET?.T STATTO? S 4 'THREE 5 T't-AQF-1A2 f gh 6 TM-AQF-16Al i ' g,"g 73 7 n:-AQF-10A2 CONE'.lAGO 8 Ut-AQF-9Al CREEK 9 TM-AQF-933 EASHCRE ISIA!O YORK I HAVEN DAM
^ . . FLO'J BRIDGE ) IhTAKE [ DISCHARGE 500 rs b Figure 2.1-1.
location of trapnet and seine stations in the vicinity of TMINS. 1565 134
86 D tD m r , , 4 h WhsQ 3.0 yACRolmT3 rEBRATr9 The ETS Section 4.1.lE requires semi =onthly samples to be taken at five staticus in the vicinity of TMI:s Apr'il through October. Replicate sa=ples were taken both inside and outside of the ther=al plume. 3.1 FETHODS Location and description of cacroinvertebrate, sampling stations are given in Table 3.1-1 and Figure 3.1-1. Four quantitative sa=ples were taken at each station with a 23 x"23 cm (529 cm 2) Ponar grab sainpler. Sa=ples were returned to the lab, washed through U.S. Standard No. 30 mesh screens, and preserved in a mixture of 10'; formalin and rose bengal stain. The stain facilitates sorting of macroinvertebrates from the detritus or sedi=ent present in the sa. ple (hason and Yevich 1967). Macroinvertebrates were sorted from each sa=ple with unaided eye. Gligochaetes and chironomids were re-sorted under a stereo microscope '10X-15X). Many oligochaetes were damaged uben the sa=ples were washed; those with a complete anterior end were counted. Every tenth Lir,nodrilus picked from the sa=ple was selected for species determination. Tubificid wor =s used for identification were cleared in A=an's lactophenol and counted on microscope slides in CMC-9 or Hoyer's reunting media. Naidid wor == were cleared when counted directly in CMC-9 or Hoyer's mounting media. Chironomids were cleared in a warm 5 to 10". solution of KOH and counted on microscope slides in CMC-9 or Hoyer's =cunting mrdia. 1565 135
li((n lH \ n a 87 ]hij l Organis=s vere dried in a drying ' oven at 55 C for 24 hr, cooled in a desiccator, and weighed to the nearest 0.1 =g on a Mettler H31 balance. Gastropods were decalcified in a 7 to 8 M solution of liCL and pelecypod shells were r*e=oved manually prior to weight deter =inations. k' eights were not deter =ined for individuals less than 0.1 cg or those retained for taxono=ic pu'rposes. 3.1.1 TANONOMC TREAnn't
. Speci= ens were identified to genus or species when possible. For diversity calculations, taxono=ic ce=parisons were =ade by the nurber of taxa, where a taxon represents the lowest level to which an organis= vas identified.
Flatwor=s (Turbe11 aria) contract when teserved directly in for=alin, which renders species identification difficult. For this report, they were deter =ined to the class Turbe11aris. The phyla Ne=ertinea and Ne=stoda were treated si=ilarly. Nurbers and bie= ass were not calculated for entoproces and bryozoans because of their colonial nature. Identification of oligochaetes is dependent on external and internal organs. Most Enchytraeidae, Naididae, and the tubificids Aulodrilus, Branchiura, Pelescolex, and Li=nodrilus udekemianus can be identified by their so=atic chaetae (hair-like structures present on all oligochaetes except the order Sr nchiobdellida) or external structures at all stages in their develop =ent. Sey.ually mature speci= ens are needed for species identifications of cost Liemodrilus, L edrilus, and Tubifex. Li'qJrilus was the only tubificid collected possessing only bifurcate crotchet chaetae; 1565 136
Dg - 8 U
\ G[16 l i y;!!T i ,IN %': rf 3! c 1 '
ug%dd , "!,l ' Tivodrilus and Tubifex additionally possess capilliform chaetae. All i=ature cubificids without capilliform chaetae were assumed to be imature L!rnodrilus_. Of the sexually nature Lienodrilus encountered . during the sa=pling period, 887. were L. hoffreisteri; i::::ature Linnedritus were grouped with L. hof f eisteri for interpretation of data. I::=ature
. Ilvedritus and Tubifex collected were recorded as i=ature tubificids with capillifom chaetae. For data analysis, these were grouped with I. tecoletent and I. tubifex and calculated on a percentage basis frc the nueber of sexually cature specimens collected at each station.
Certain species of earthworms (limicolous) inhabit the margins of streams, ponds, lakes, etc. (Reynolds 1975). Limicolous earthwor=s encountered unidentifiable to the family Lumbriculidae or Sparganophilidae were record, I as "=egadriles" (a tem witich collectively encompasses cany fasilies of earthwor=s). Leeches (Hirudinea) contract when preserved directly in for=alin, which cakes identification difficult. Large, m;ture specimens are rieeded for genus and species determinations in the family Erpobdellidae; i=ature or badly distor'ed spe::icens were identified only as Erpobdellidae. Pooreobdella rie-este-2 was the only erpobdellid collected identifiable to species. Individuals of 3. eierosto a were grouped with Erpobdellidae for diversity calculations. Nu=hers of larval and pupal Diptera were co=bined for data interpre-tation. If keys were unavailable or incomplete for species separation in so=e genera, apparently different species of a genus were given letter designa-tors (i.e., Eukiefferiella sp. A, sp. B, etc.). Soce genera or species are 1565 137
?dQ q, 89 h %L ' l'g ,!)/ f)
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separable only to groups. The Palpo via group (Diptera: Ceratopogonidae) contains the genera Fezzia, Prohezzia, and Palpouvia, which are inseparable ~ in their larval stages at the present time. Species identifications in the Chironocidae' are dif ficult. Roback (1976) found many identifications of im=atures and adults (by various authors, including himself) were incorrect or nocenclatorially out of date. Major genera and groups constantly undergo revision. Consequently, so=e specimens identified previously =ay have been misdetercised. Misdeterminatione in Kennedy (1975) and Polk and Epler (1976) were: Limnodrilus erofundicola (1975, 1976) = L. hoff eisteri (this report) Trepobates sp. = "etrobates hesperius Micropsectra sp. = Tanvtarsus sp. Synonomies fro Polk and Epler (1976) are: Athripsodes = ceraclea (cf. lbrse and Wallace 1975) Ablabese ia surf ensis = 3,. mallochi (cf. Roback 1971) Chirononis attenuatus (as Chironomus sp.) = .C.. decorus (cf. Sublette and Sublette 1974). Specimens identified to tribe Tanytarsini in Polk and Epler (1976) were Tam tarsus sp. Macroinvertebrate taxa found in the Susquehanna Rivar in the vicinity of Three >Cle Island are listed in Table 3.1-2. Identification of benthic organis=s was aided with keys and descriptions in Beck and Beck (1966), Beck and Beck (1969), Boesel (1974), Brinkhurst and Jasieson (1971), Brown (1972), Burch (1973), Burks (1975), Curry (1958), Ed:nondson (1959), Foster 1565 138
90 (1972), Harman and Berg (1971), Hilsenhoff (1975), Hiltunen (1973), Holsinger (1972), Johannsen (1969), Kle=a (1972), Mason (1973), Needham and Westfall (1955), Reynolds (1975), Roback (1957,1974b,1976), Ross e (1972), Saether (1975, 1976), Sawyer (1972), Usinger (1956), talker (1958), and Walker and Corbet (1975). 3.1.2 DATA ANALYSIS Densities (nu=ber/c2 ) were calculated for taxa that cocprised more than one percent of the total nu=ber of organisms collected. Biomass (eg/m2 ) of selected taxa was determined. Diversity indices are used to analyze co== unity structure. Monthly esti=ates of diversity (infor=ation per individual) as defined by Shn - n's for=ula: s D=[ nt/N1og2 "i/N i=1 vere ce=puted for each station using the for=ula: D = C/N (N1cgloN - [ngog10nt) l where D = infor=ation per individual, C = 3.321928 (converts legio to logy), N = total nu=ber of individuals, nt = total nu=ber of individuals in the ich species, s = the nu.ber of species in the sa=ple for a acation (Lloyd et al. 1958). This index su arizes the nu=ber of taxa present and the distribution of individuals a=ong the taxa. Iov D values result from a s=all number of taxa and uneven distribution of individuals. Large nu=bers of taxa and even distribution of individuals result in high D values. 1565 139
91 Benthic co:= unities at each station =ay have similar D values, but differ in species cortosition. The similarity in species co= position between stations was investigated by an index of percent similarity - (Whittaker and Fairbanks 1958). This index is expressed as: PSc=100-0.5{a-bl . where JSc is the percent similarity and a and b are the percentages of a species in sa=ples A and B. This is a quantitative =casure of the relative
. similarity of species co= position in cuo sa=ples. The PSc is only an e=pirical ceasure and is not an esti= ate of a statistical para =eter of the population from which the sa=ples are drawn. Values range fro = 0 to 100.
A value of 0 indicates the species co= position is entirely different and a value of 100 indicates co=plete similarity between the two sa=ples. Analysis of variance (ANOVA), randomized block design (Sokal and Rohlf 1969), was perfor=ed to co= pare nu=bers of taxa between stations and assess changes over time. The Student-Nev=an-Keuls multirange test ('ioolf 1968) was performed if significant differences existed in the A';0VA. The multirange test was designed to specify which sa=ple =eans (y) differed significantly from each other. Changes in populations of Li modritus hoffreisteri for the 1974 through 1976 sample dates were examined; a three-factor ANOVA was used (Sokal and Rohlf 1969). Co=parisons were made for years, sa=ple dates, the cacroinver-tebrate stations, and interactions between these factors. No quantitative data was available for April 1974 at Station 11A2. The ANOVA vas performed 1565 140
92 on data collected from May through October 1974, 1975, and 1976. Numbers of L. erofundf eela cisdeter=ined in 1974 and 1975 were included with L. h, of' elstert in the analysis. The distribution of benthic organis=s is clu= ped rather than rando=; a logarieh fe transfor:ation [ log 10(y+1)] was used on densities of
- 1. hoff etateri for each replicate to nor=alize the data (Elliot 1971).
Logarith=ic transfor:ation prevents attention being focused on s=all variations in nu=hers which cay..not be statistically significant (Brinkhurst and Ja=ieson 1971). The Student-Nev=an-Keuls multirange test (P = 0.05) was e=ploytd if differences were indicated. 3.2 Rest *Lis Results of April through October cacroinvertebrate collections are reported in Tables 3.2-1 through 3.2-35. A total of 90,567 specimens (112 taxa) was taken during 1976 (Table 3.2-36). The three cost abundant taxa (84.8* of the speci= ens) were Li=nedritus hof fmeisteri (65,516 sper '= ens, 72.37.), chirono- 2 s decorus (9,084,10.0".), and Nais elinzuis (2,255, 2.5?.). Other taxa that cocprised more than 17. of the total were Pisidium sp. (1,646 speci= ens,1.87.), Procladius sp. (1,199,1.37.), Gaemarus fasciatus (1,084, 1. 27.) ,' L. elaearedeianus (1,059, 1.27.), and L. udekemianus (912,1.0"). L'_nodritus hoff eistert was usually the most abundant organism collected at each station (Table 3.2-36 and Figure 3.2-1). Nais eitneuis was most abundact at Station 1Al in May and chirocoms decorus was cost abundant at Station 931 in May and at 1A2 in June. 1565 141
93 The freshwater polychaete, Manavunbla speciosa, was collected for the first ti=e in 1976. 3. nocciosa has been taken from the Susquehanna River in Conowingo Pond (D. Wahl, Ichthyological Associates, Inc., personal cormu11 cation)F Formerly believed to be rare, recent papers (Ililtunen 1965; Poe and Stefan 1974; Spencer 1976) have shown 3. speciosa to be co:znon and abundant (over 45,000/m2 in 1.ake Erie) in many areas. Its small size * (< 3 en) probably caused it to be overlooked. Iligh numbers of the limpet Terrissia were collected at Stations lAl and 1A2 on 19 October 1976. The reason for the high nu=bers was not readily apparent. The limpets may have drifted to Stations lAl and 1A2 from rocks located upstrea:n. 3.2.1 DENS ITY Densities of benthic macroinvertebrates were dominated by a few taxa (Table 3.2-37). 1ienodrilus hof f eisteri was most abundant and ranged from 390/m2 (Station lA2 in April) to 9,776/m2 (Station llAl in October). Feak densities occurred in June at Stations lAl, llA2, and 931 and in Septe ber at IA2. Iowest densities occurred in April at all stations. Peak densities of Chiror.ow decorus occurred at all stations in June. The greatest density (4,863/m2 ) was at Station 9Bl. No C. decorus were collected at Stations lA2, lla , and 9B1 in April, and at ilAl in October. Nais elinguis reached a peak density of 4,612/m2 at Station lAl in P.ay. No N. elinculs were collected af ter June. 1565 142
-/)l 3.2.2 BIFASS At most stations and :enths the pleuroceril sr. ail. "cniobasis vireinica, co= prised the greatest bio = ass and peaked at 8,73.'..*- =g '=2 at Station 11A2 .
in Septerber (Table 3.2-36). The greatest bio = ass (2,103.3 =g/=2) for L. hof'- elsteri occurred at 11A2 in June. C,. deco-:s occueighed all organisms at Station 931 in Y.ay and June, and peaked (3,022.4 =g/=2) in June.
. 3.2.3 DIVEDSITY (M N nthly D values at "ach station ranged fro = 0. M to 2.76 (Tr.ble 3.2-39).
The lovest D value (0.56) occurred at Station 931 in A;ril; L. hoff=eisteri co= prised 91.3'?. of the organis=s in the sa=ple. S e hig* nest D value (2.76) occurred at lA2 in Y.ay; L. hef
- eisteri accounted fer :=ly 42.8~, of the sm::ple. D values were generally higher at Station *.A1.
3.2.4 PFD.CE! r SDf11. ART 3' CPPOSITION N=bers and percent co= position of benthic orge-* e and calculated PSc indices are presented in Tables 3.2-36 and 3.2-40, resTectively. The Pse value.; vere in the inter =ediate to high af finity rarge ( >50". si=ilarity). Index values indicated that Stations IA2 and 931 rere -l e ost si=ilar; Stations lAl and llAl vere the least si=ilar. The ??c values indicated that IA2,11A1,11A2, and 931 vere more similar in their faunal associations with each other than with Station lA1. 3.2.6 A?MLYSIS OF VARTANCE Results of the ANOVA (rando=ized block design) for -- ~'er of taxa revealed significant differences (P = 0.05) between stations and sa=ple 1565 143
Iaj' 1 dates (Table 3.2-41). Application of the Stude:t-::ew=an-Kouls cultirange test (P = 0'.05) between station ceans (7) indicated Station 1Al was significantly different fro = the ocner stations ar.d possessed the greatest
=ean nu=ber of taxa (Table 3.2-42). Station IA: vas similar to 9P,1 and ,
Station 11A1 was similar to 11A2 and 9B1. Statica 1A2 differed significantly from 11A1 and 11A2 in nu=ber of taxa. The cultirange test performed on nu=bers of taxa between sa ple dates showed no significant difference between the two sa=ple dates for each month (Table 3.::-43). Ce:parison of nu=ber of taxa by month revealed that the 6 April date was significantly different frc= the 4 and 18 2'ay dates and the 20 April date differed from 41:ay, but was si=ilar to 18 l'ay. The number of taxa taken on 4 !!ay was different from the - ~ er' taken on 1 June, and similar to 15 June. The 18 I'.ay date was si=ilar to both June dates. 2.t=bers of taxa collected on 1 June differed from both J:1y dates and 15 June was similar to both July dates. No significant difference was indicated when co= paring July to August, August to Septe=ber, a=d Septe=ber to October. The lowest number of taxa was recorded on both April dates. Nu=bers of taxa collected in !!ay and June were highest. Results of the three-factor ANOVA for populations of Li nodrilus hoff eisteri revealed significant differences (? = 0.05) between years, benthic sa=ple dates, stations, and the interaction between these factors. The station factor had the greatest effect on densities of L. hoff eisteri (Table 3.2-44). 1565 144
96 The Student ' ev=an-Keuls multirange test perfor=ed on year = cans revealed all three years were significantly different. Mean densities of L. _hoffr.eisteri were highest in 1976 and levest in 1974 (Table 3.2-45). e Application of the cultirange test to sample dates showed no significant differences between densities on the two dates sa= pled each month (Table 3.2-46). Cocparison of densities by conth revealed that the first and see:25 May sa=pling dates differed from the first and second June dates. Both June dates had densities similar to the two July dates. Densities for the first July date were significantly different from the first August date and the second July date differed from both August dates. The density for the first August date differeci from both September dates and the second August date was similar to the Septe:ber dates. Both September densities differci from the two Octcber densities. Densities of 1. hof freisteri were low duri=; October, May, and August. High densities recorded in June, July, and Septe=ber were not significantly different. The c:ultirange test applied to densities at the cacroinvertebrate stations revealed all were differect, except Stations 11A1 and 11A2 (Table 3.2-47). The two stations were similar and had the highest mean densities of the caeroinvpttebrate stations. Station 1Al had the lowest cean density of L. hof 6eisteri. N$ (@- M@u@eff s 1565 145
97 3.3 pisa:SsTON The nature of the substrate has been found to be the =bst i=portant factor that deter =ines species distribution (Brinkhorst and Ja=leson 1971;
!!ynes 1972; Mar =an 1974). Chutter (1969) and deMarch (1976) have de=en-strated that changes in substrate result in changes of =acroinvertebrate populations. Hynes (1972), ibopes (1974), Polk et al. (1976), aal Massengill (1976) concluded that high flows scour substrates and wash away =any organis=s. Passengill (1976) and Tebo (1970) found this particularly true of substrates composed of sand and silt (cud) where finer sedi=ents are vashed away, leaving sand. Shifting substrates create an unstable habitat (Chutter 1969; Tebo 1970). Massengill (1976) found that ice affects substrates, particularly those co= posed of sand.
Substrates at Stations 1Al and 1A2 were basically si=ilar (Table 3.1-1). Substrates at Stations 11A1 and 11A2 were co= posed of ce=pacted =ud with coal and fine sand over a gravel substratum. The substrate at Station 931 consisted of cud. During high flows, silt and allochthanous caterials were washed away, leaving behind the heavier caterials. The substrate of Station 1Al was more susceptible to changes in river flow. Ice exerts a heavy influence on the substrate at Stations 1Al and 1A2. Effects of ice were not as severe at Stations 11A1 and 11A2, where operation of TMI::S leaves the area free of ice. In the spring, ice break up subjects Stations 11A1 and 11A2 to ice scouring. Conditions at Station 931 vary fro = open water to ice cover; the substrate is subjected to scouring. fb
98 The dominant organism at all stations was t.fr.nodrilus hafbeistert. Brinkhurst and Ja=ieson (1971) found L. hof freisteri to be the most abundant organiss in sh:rreline areas with soft sedf=ents. Carr and !!iltunen (1965) found that alundance of tubifirid wor =s was related to organic enric! cent of the substrate. Polk et al. (1976) and results of the three-factor A:.tWA indicated that Station 1Al produced the lowest density and was significantly different from the other stations. The unstable, abrdsive, and organically poor sand and coal substrate at 1A1 cay acccune for the low density. SLsilar densities at Stations 1A2 and 9B1 (Polk et al.1976) could be attributed to the similarity of habitat; both stations are backwater areas during low flow. Stations 11A1 and 11A2 produced the highest densities and the three-factor A!DVA revealed they were not significantly different. The close proximity and like substrate cay account for the similarities at these stations. The three-factor A :0VA revealed populations of L. hof f cisteri were highest in early June. Densities were lowest in : fay and October: periods cost affected by ice or high river flow. rennedy (1966) found that ice cover caused cessation of winter breeding activity in L. hof f ef steri. Stations significantly affected by flood waters were 1A1, 1A2, and 981 (Polk et al. 1976). Chironomid populations were affected by substrate and reproductive cycles. Polk et al. (1976) fcund chiron mas populations were affected by the Septe=ber 1975 flood waters (llurricane Eloise). Chirononids are holo = eta-bolous insects, and population fluctuations are caused in part by pupal 1565 147
99 e=ergaace (adults are not aquatic). F.epr9d uctive cycles for so e chirc rrr. ids range from several generations a year to one every two years (?.d u.'< 1974a). Interspecific co= petition is reduced by stag;,ered breeding period.g (?.eid 1961; Grant and !'ackay 1969), and could account for high u=hers of Orthocladiinae in the spring, and Chironominae later in the year. Icv numbers of S. decorus were observed at Station 11A1, April - throeth October 1976. Reasons for lov :r.:=bers of C. decorns were not appare= . Leeches were =nst abundant at Stations 11A1 and 11A2. ::e=bers of the geare FalMella are known to feed on =ollusks (Sawyer 1972; Kle r: 1975, 1979 . Specicens of Helobdella vere often found inside the shells of the s= ail e-n iobast= virrinica. This snail possesses an operculum, a hard shell-like disc which closes the shell aperture. Kle::s (perscnal coani-catics, believes the leeches =ay use the shells as an attach =ent substrate, as s: ails preyed upon by Helobcella are non-operculate. :'.aloney and Chandler (1976) reported that E. lineata feeds on Coniobasis under labera-te: r ceditions. The greatest nu=ber of *delohdella collected coincided with t e greatest :re.ber of Coniebasis collected at 11A1 and 11A7 in 1576. Ir;chdellid leeches were collected only at Stations 11A1 and 11A2. Saw er 11374) states "no other single factor is more important in rostrfc-ting the distribution of freshwater leeches than the availability of food orra=Is s". Erpohdellids are predacious on oligochaetes and insut larvae. 011;xhaete nu=bers were highest at 11A1 and 11A2. 1565 148
D 1h </^/ O 6
~{} Gl lf%l~dir llUulvlfl9Q , :
Spatial (station) co=parisons ade with 1976 data indicated that Sts : ion 1Al differed from all other stations in nu=ber of taxa and species cos.osition. This was due to substrate variability and drif t frem upstrezs 1cc tions. Station 1A2 was similar to irl in number of taxa and species
, eco osition (917. similar); this c.2y ham resulted from similarities in hab tat most of the year. Stations 1111 and 11A2 were similar in~ nu=ber of exa and species co= position (S**. si=ilar); this cay be caused by sta ton proximity and substrate si=1!srity.
The benthic coc=: unities had hip Wers of taxa in P.ay and June (Fi ure 3.3-1). This was attri5uted to seasonal al undance of naidid vor=s acc orthocladiinid Chironomidae. Naidids, especially the genus N.11s, mature siraltaneously in the spring. Populatie:s reach a maximum in June, then die of' rapidly due to degeneration of the digestive tract caused by reproductive at :ivity (loden 1976). The seasonalier of caldids at Three Stile Island c neurs with Loden's werk. L'thlm (1970) collected data frca - *rous authors and found, in gener.al, S
. hat diversity (D) values less than ene wre indicative of " stressed" co:=: unities. Values greater than three vere indicative of comnities asscelated with " good-excellent" water g ality. Ischiger and Nalepa (19o6) attributed low diversity of benthic face.a to low habitat diversity rather than poor water quality. Trends in ? values along Three 1111e Island from 1974 to 1976 indicated " poor" to " geed vater quality or habitat diversity (Table 3.3-1, Figore 3.3-2). D values -vre generally higher at Station IA1, where conditions were " good". Statiets 1.C and 981 displayed generally " fair" values, while 11A1 and 11A2 fluct.ated from " poor" to " fair".
1565 149
101 No apparent effects on benthic co=sinities at Stations llA1, llA2, and 9B1 ware noted due to the shutdot.] of TMINS for refueling (21 February to 27 May 1976) or the dredging operations in front of the Intakes for Units 1 and 2 (August through Septe=ber 1976). Trace amounts of oil vere present in most sa=ples at all stations. No effects of oil on macroinvertebrates have been observed. In su==ary, the variability of the substrate influenced by river flow - and ice exerts more stress on the benthic co=: unities along Three Mile Island than the operation of TMINS. This cor.pletes the =acroinvertebrate require-ments of the ETS for Unit 1; the progra= will be continued as specifiec in the ETS for Unit 2. Beck, E.C., and W.!!. Beck, Jr. 1969. Chironomidae (Diptera) of Florida. III. The Marnischia co= plex (Chironominae). Bull. Fla. St. !bs. 13(5):277-313. Beck, W.H., Jr., and E.C. Beck. 1966. Chironomidae (Diptera) of Florida: I. Pentaneurini (Tanypodinae). Bull. Fla. St. Mus. 10(8):305-379. Boesel, M.W. 1974. Observations on the Coelotanypodini of the northeastern states, with keys to the known stages (Diptera:Chirono=idae: Tan)podinae). J. Kans. Ent. Soc. 47(4):417-432. Brinkhurst, R.O., and B.C.M. Jamieson. 1971. Aquatic Oligochaeta of the world. University of Toronto Press, Toronto. 860 pp. Brown, H.P. 1972. Biota of freshwater ecosyste=s identification canual No. 6. Aquatic dryopoid beetles (Coleoptera) of the United States. U.S. Govern =ent Printing Office, tiashington, D.C. 82 pp. Burch, J.B. 1973. Biota of freshwater ecosyste=s identification =anual No. 11. Freshwater unionacean cla=s (Mollusca: Pelecypoda) of North America. U.S. Goverc=ent Printi:.g Office, !!ashington, D.C. 175 pp. 1565 150
102 Eurks, B.O. 1975. The mayflies, or Ephemeroptera, of Illinois. published in 1953 as Illinois Nat. Hist. Survey, Bull. 26(1).](First Reprinted by Entomological Reprint Specialists, Los Angoles, California. 216 pp. Carr, J.F., and J.K. Hiltunen. 1965. Changes in the bottom fauna of western Lake Erie from 1930 to 1961. Limnol. and Oceanogr. 10(4):551-569. Chutter, F.M. 1969. The effects of silt and sand on the invertebrate fauna of streams and rivers. Hydrobiologia 34(1):57-76. Curry, L.L. 1958. Larvae and pupae of the species of Crvotochironoras (Diptera) in Michigan. Li=nol, and Oceanogr. 3(4):427-442. deF. arch, B.C.E. 1976. Spatial and temporal patterns in =acrobenthic strean diversity. J. Fish. Res. Board Can. 33:1261-1270. Edmondson, W.T. (editor) 1959. Freshwater biology. Second edition. John Wiley and Sons, New York, New York. 1248 pp. Elliot, J.M. 1971. Some methods for the statistical analysis of samples of benthic invertebrates. Freshwater Biological Association Scientific Publication No. 25. A=bleside, Westmortdad, U.K. 144 pp. Foster, N. 1972. Biota of freshwater ecosyste=s =anual No. 4. Freshwater polychaetes (Annelida) of l brth America. U.S. Govern =ent Printing Office, Washington, D.C. 15 pp. Crant, P.R. , and R.J. tiackay. 1969. Ecological segregation of systematically related stream insects. Can. J. Zool. 47:691-694 Har=an, W.N. 1974. Snails (Mollusca:Castropodai, pp. 275-312. In C.W. Hart Jr. and S.L.H. Fuller (editors). Pollution ecology of freshwater inver-tebrates. Academic Press, Inc., New York, New York. Har=an, W.N., and C.O. Berg. 1971. The freshwater scalls of central New York with illustrated keys to the genera and species. Cornell Univ. Ag. Exp. Sta., Ithaca, New York 1(4):1-63. Rilsenhoff, W.L. 1975. Aquatic insects of Wisecasin. Technical Bull. No. 89. Dept. of Natural Resources, Madison, Wisconsin. 53 pp. Hiltunen, J.K. 1965. Distribution and abandance of the polychaete, Manavunkia speciosa Leidy, in western Lake F_rie. Chio. J. Sci. 65(4):183-185.
. 1973. Keys to the tubificid and naidid 011gochaeta of the Creat Lakes region. Second edition. Creat Lakes Fishery Laboratory, Ann Arbor, Michigan. 25 pp.
1565 151 32 01UE
103 p- -?
!!olsinger, J.R. 1972. Biota of freshwater ecosystems identification manual No. 5. The freshwater a=phipod crustaceans (Camaridae) of North America. U.S. Coverrc ent Printing Office, k'ashington, D.C. 89 pp.
Itoopes, R.L. 1974 Flooding, as the result of Eurricane Agnes; and its effget on a cacrobenthic coc= unity in an infertile headwater streas in central Pennsylvania. Linnol. and Oceanegr. 19(5):853-657. Hynes , II. B.N. 1972. The ecology of running waters. University of Toronto Press, Toronto. 555 pp. " Ischinger, L.3. , and T.F. Nalepa. 1966. Water Pollution: Freshwater Macro-invertebrates. J. Water Pollut. Contr. Fed. 48(6):1318-1335. Johannsen, 0.A. 1969. Aquatic Diptera. (First published in 1934, 1935, 1937, and 1937 as Parts I through IV. Memoirs 164, 177, 205, and 210 Cornell Univ. Exp. Station). Rei !inted by Entomological Reprint Specit. lists, Los Angeles, Califor ia. 369 pp. Kennedy, C.R. 1966. The life history of Li-modrilus hoffr eisteri Clap. (011gochaeta:Tubificidae) and its adaptive significance. Oikos 17:158-168. Ker.nedy, J.H. 1975. Macroinvertebrates. pp. 339-386. In W.A. Potter and Associates. An ecological study of the Susquehanna River in the vicinity of the Three !;ile Island Nuclear Station. Annual Report for 1974. Ichthyological Associates, Inc. 46S pp. Klem, D.J. 1972. Biota of freshwater ecosyst r_s identification canual No . 8. Freshwater leeches (Annelida: Hirudinea) of North America. U.S. Govern =ent Printing Office, Washington, D.C. 53 pp. 1975. Studies on the feeding relationships of leeches (Annelida: Hirudinea) as natural associates of collusks. Sterkiana (58):1-50; (59):1-20. 1976. Leeches (Annelida: Hirudinea) found in North America mollusks. Malac. Rev. 9:63-76. Lloyd,M., J.H. Zar, and J.R. Karr. 1968. On the calculation of information-theoretical measures of diversity. Acer. Mici. Nat. 79(7):257-272. loden, M.S. 1976. Life history patterns of naidid oligochaetes in Indiana streams. Paper presented at the 24th meeting of North A=erican Benthological Society, Lacrosse, Wisconsin, Parch 24-26, 1976. Maloney, S.D., and C.M. Chandler. 1976. Leeches (Hirudinea) in the upper Stones River drainage of middle Tennessee. A=er. Midl. Nat. 95(1): 42-48. 1565 152
104 }kson, V.T. 1973. An introduction to the identification of chironomid larvae. ':nviron= ental Protection Agency, Cincinnati, Ohio. 90 pp. 11ason, tJ.T. , and P.P. Yevich. 19,67. The use of phloxine B and rose bengal stains to facilitate sorting benthic sa=ples. Trans. Amer. Iticros. Soc. 86(2):221-223. Massengill, R.R. 1976. Benthic fauna:1965-1967 versus 1968-1972 pp. 39-53. In D. Merri=an and L.}!. Thorpe. The Connecticut River Study. The Icaact of a Nuclear Power Plant. Am. Fish. Soc. >bnogr. 1. 252 pp. Morse, J.C., and I.D. tJallace. 1975. Athrfosodes Billberg and Ceracles Stephens, distant genera of long-horned caddis-flies (Trichoptera: Leptoceridae). Proc. of the First Inc. Sy=p. on Trichoptera. Junk. The IIague. pp. 33-40. Needham, J.G. , and !!.J. tJestfall, Jr. 1955. A canual of the dragonflies of North A= erica (Anisoptera), including the Creater Antilles and the provinces of the ?!exican border. Univ, of California Press, Berkeley and Los Angeles. 615 pp. Poe, T.P., and D.C. Stefan. 1974 Several environ = ental factors influencing the distribution of the fresh-water polychaece, Manavunkic specioea Leidy. Chesapeake Sci. 15(4):235-237. Polk, J.L., and J.H. Epler. 1976, Macroinvertebrates. pp. 241-298. In IJ.A. Potter and Associates. An ecological study of the Susquehanna River in the vicinity of the Three Mile Island Nuclear Station. Annual Report for 1975. Ichthyological Associates, Inc. 395 pp. Polk, J.L. , J.H. Kennedy, IJ. A. Po tter, and J.II. Epler. 1976. The effects of flooding on populations of Chirono ,s Meigen (Diptera: Chironomidae) and Limnodritus Claparede (011gochaeta:Tubificidae) in the Susquehanna River in the vicinity of Three Mile Island, Pennsylvania. Proc. Pa. Acad. Sci. 50(1):91-95. Reid, G.K. 1961. Ecology of inland waters and estuaries. Van :ostrand Reinhold Co. , New York, New York. 375 pp. Reynolds, J.tJ. 1975. Soar:snonhilus neareet n. sp. (Oligochacta:Spargano-philidae) a nearctic earthworm from western North Carolina. Itegadrilo-g ica. 2(2):9-11. Roback, S.S. 1957. The i : .aturc tendipedids of the Philadelphia area. Monogr. Acad. Nat. Sci. Philad. No. 9. 180 pp.
. 1971. The adults of the subfa=ily Tanypodinae ( = Pelopiinae) in North America (Diptera: Chironomidae). Monogr. Acad. Nat. Sci. Philad.
No . 17. 410 pp. 1565 153
105
. 1974a. Insects (Arthropoda:!nsecta), pp. 313-376. In C.W. Hart, Jr. and S.L.H. Tuller (editors). Pollution ecology of freshwater invertebrates. Acade=ic Press, Inc. , New York, New York.
. 1974b. The i=ature stages of the genus coelotanvoun (Chironocidae:
Tanypodinae:Coelotanypodini) in North America. Proc. Acad. Nat. Sci. Philad. 126(2):9-19. , 1976. The i=ature chironocids of the eastern United States. I. Introduction and Tany, iinae-Coelotanypodini. Proc. Acad. Nat. Sci. Philad. 127(14):147-210. Ross, H.H. 1972. The caddis flies, or Trichoptera, of Illinois. First published in 1944 as Illinois Nat. Hist. Survey, Bull. 23(1) .] [. Reprinted by Ento:nlogical Reprint Specialists, Los Angeles, California.
. 326 pp. - Saether, 0.A. 1975. Nearctic and Palaearctic Heterotrissoeladius (Diptera:
Chironocidae). Eull. Fish. Res. Board Can. 193. 65 pp.
. 1976 Keys to larvae and pupae of Orthocladiinae and Tel=atogeto-ninae. 61 pp. (Unpublished).
Sawyer, R.T. 1972. North American freshwater leeches, exclusive of the Piscicolidae, with a key to all species. Illinois Bio.1:enogr. 46. 154 pp. 1974. Leeches (Annelida: Hirudinea) pp. 81-142. In C.U. Hart, Jr. and S.L.H. Fuller (editors). Pollution ecology of freshwater inverte-brates. Academic Press, Inc., New York, New York. Sokal, R.R., and F.J. Rohlf. 1969. Biometry, the principles and practice of statistics in biological research. W.H. Freeman, San Francisco. 776 pp. Spencer, D.R. 1976. Occurrence of Manavunkia speefosa (Polychaeta:Sabe111dae) in Cayuga Lake, New York, with additional notes on its North American distribution. Trans. A=er. Micros. Soc. 95(1):127-128. Sublette, J.E. , and 1:.F. Sublette. 1974. A review of the genus Chirono-us (Diptera:Chironocidae) V. The escurus-complex. Stud. Nat. Sci. 1(8):1-42. Tebo, L.B., Jr. 1970. Effects of siltation, resulting from i= proper logging , on the bottom faunt of a small trout stream in the southern Appalachians. The Prog. Fish-Cul. 17(1955):54-70. Usinger, R.L. (editor). 1956. Aquatic insects of California with keys to North A=erican genera and California species. Univ. of California Press. Serkeley and Los Angeles. 508 pp. 1565 154
106 Walker, E.M. 1958. The Odonata of Canada and Alaska. Volu=e Two. Part III: the Anisoptera - four families. Univ. of Toronto Press, Toronto. 318 pp. Walker, E.M., and P.S. Corbet. 1975. The Odonata of Canada and Alaska. Volume Three. Part III: the Anisoptera - three families. Univ. of
. Toronto Press, Toronto and Buffalo. 307 pp.
Whittaker, R.H., and .%'. Tairbanks. 195'S. A study of plankton copepod communities in the Colu=hia Basin, southeastern Washington. Ecology 39:46-65. Wilks, J.L. 1970. 1.ange of diversity index in beathic macroinvertebrate populations. J. Water Pollut. Contr. Fed. 42(5) Part 2:P.221-224. Woolf, C.M. 1968. Principles af bio =etry. Van postrand Co., Lts., Toronto, Canada. 359 pp.
b Table 3.1-1 Location and description of =acroinvertebrate stations. Station :1=her .. Location'and rescription n:-AQI-1Al* 400 09' 52" N, 76 43' 26" W. Ibrth end of Sand Beach Isla d, 30 to 75 m offshore.
, Water depth varied fro = 0.5 to 2.0 =. Substrate co= posed of sand, coal particles, and de:-itus; someti=es with =ud and/or clay. Trace a=ounts cf cil sometimes presen:.
TM-AQI-1A2 . 400 09' 36" %, 76* 43' 30" W. . Southwest St. .ichn s Island,1 :o 15 m offshore at =outh of channel be:veen T:!I and St. _chas Island. Eater depth varied from 0.5 to 1.5 =. Substrate co= posed
=ostly of sand, coal particles . e, and detritus; so=etimes with gravel or clay, race amounts of oil so=etimes prese t.
n!-AQI-11A1 40* 09' 09" 7, 76* 43' 39" W. I to 10 m downstrea= from TMI _scharge, I to 15 = offshore. .a:er depth varied :-:= 0.25 to 1.0 =. Substrate co posed of =ud cixed with coal particles, fine sand, and detritus; so=e:izes with =uck, clay, or gravel. Trace acounts of oil present. TM-AQI-11A2 400 09' 07" N, 76 43' 39" W. 70 to 75 m dov:strear from n 2'scharge, I to 15 = offsher . Water depth varied fr:= 0.25 to 1.5 =. Substrate co pesed of nid with fi e sand, some ceal particles, and detritus; so=a:i=es with clay. Trace a=ounts of oil present. ni-AQI-9B1 400 08' 03" N, 76* 43' 33" W. 1900 m downstrea= fro = n:I rischarge, 5 to 15 = offshore. Water depth varic3 frc= 0.75 :o 1.5 m. Substrate co= posed of =d vich ruck, de:ri:us, and fine sand, with some coal particles. Trace a=u=ts of oil present.
- Polar coordica:e prefix T'l-AQI- deleted fro = all static: =u=bers for discussion in text.
1565 156
Taste 3.1-2 108 P.arrotavertebrates takes from the Susquahatma River in the vicinity of Three *tte Island. Coeteaterate fydrones Mirudiosa Eydroida IAync hobdel t ida Nydridae Classiphea11dae D,f,t3 sp. *e leNell a rifer.sta (Castle) 174monedusa !!. IlmeJTa t oer 111 0 O!!adiadidae Pfewd**lin s otifer) Note Craisednasta save dvi Lasiester 2. rarestet a p ay) Fiscase11 aa P!aryhelminthes **ro%*.ella tvi:drf s Leidy
?artellaria Pharyndobde1115 Trictadtda tryobdeltidae Planar 11dae trxMel'a metata (letJyl h&g,11g t!t!t*,a (*1rard) tweeewei a -te
- s e s n Cbore)
Escartinea Artirepsia
- Impta ArachaLJa Nplosenertial A aceae Tetrastercatidae Pisauridae Presto a m (141dy) Hvorac arana cle rus trit M CJalskenaer)
Me:stoda crustac ea a Copepoda
- as a-h ephala Lernacidae Palaeac anthocephala lertars sp.
F,chlacchynchidae Branchtura testar$v9evi!es t'e:ar.s (Lintos) ArrJ1.s cat;st?-1 Dana and Herrick taopoda Eataproc ta Asellidae Ernatellida Asellus e vrvtte say tlrnatellidae Ac:ph t poca l'rnatttia treetlis Letty Crar.refra sp. tryo:ma pecapoca ca:arus fasciatss say F5ylactolasmata taphopodidae Aatacidae Lcabao *et ta certe-1 ("vett) (*reameetes et?tJrts (Hageal Pecetaatet ta razei:1.a (Leidy) 2. ris, m Warara) Plumste1114ae losetta Colle= bola Fvalf*elen racctets i?ancock) Ephemeret tera Pluma'ella Lt:,g_1 (Liscasus) Cy molasma ta 51phloauridae
**** * #* Isem tMa sp.
Paludice!!!dae 5t:51o aras sp. Paluite el'a artic a' *1 (Ihreaberg) Saetidae
!sttis sp Amelifa Beptagentidae Pet erhaeta e t e ac rri c a :t t-a (Sanka)
Errantia 1 1-ter u ac eae r (Say)
$abellidae 5te9ece a e,yyta 32rsa
*anav29A ta stec t,*sa Lat.ty 1. rMe ell 2 (dalsh)
Leptop'slet tidae Clitochaeta Plesiopera 1.ert*o le%1a sp. tactytraeidae Ephacere111dae Naididae fr6=-eretta sestive McDuJnough Areteo*a f s le r-d1 O'artial 1. serve.a group sp. eulacherus N rcat.s (N11er) 1. verts -ills McDunaough Tricerytnadae Ct ser'nsseer c.a- s .s (*ruichutaea) Tri-e vesoden sp. laim tretsc'3J.1 " craelsea Carstaae
- 3. git:nts N11er
- 3. vart a* tif e Pigvet Cse9ts 11111 Eurka Pota=anchidae enterats serve-tisa OG11er) Peta aethus sp.
Paraa.ats IIlta trate 1;te:aradae Slavtr.a arntsicalara (d*tdeken) Tub 1ticidae Fevareole 114 ata (Serville) Autodettus et.rttets (Ptruet) 3. rirada .'icrunaough Hrsv htura sever?-t !addard Santiscicae Ilyertius tWets*i (32uthern) !setisen sp. L1:trk'3rtius g,trc;,e 3ricahurst odonata Aeshaidae L. cla*v erets u 1.atre! 6C41 JJilllii1 (Orury) L Fof fteinte-1 Claearede Cc-:phidae
- 1. s? traits (Lineal L. gere la .s Clapardda *Te rtMas r?tvt>q Selys Petescolet lei;.5 dises) CW.s t \r*rms) vf1 Sat es selys
- m 1***e esus (frith) *. M&ur.s ) ea s:'Js '.ais:t Tubites t.? stet (Niier) G. f M:9uss livine Salys trosopera 9. O! e.:s) s:191cers C='alsh)
P'.ac rnit da e Lu=briculidae
!ra-chlobdeltida "ac ~ *ia illimteas ts Walsh Dyisthopora Cerculticae
' tit'eca ret 9ceat Hagen S parganophil er.r. ._ t ida, e se,s.,' -
1565 157 e i cn FGMPa
=
s0 , t
Table 3.1 2 u ncinued, D , V D 7{ Uf R U J 3 ArthropoJa = c ontinued 'ry a rc s t it irse lasec ta contin. sed Phth 1;s t ..at a 'trun odonata - continued g. yJ ael.if d 191 *3 Libellulidae Limep%i a .ae LibellJia I ct.,*a tar mister genus er.
- f .t . 7 s. *attes L. g t ru r - Pvet M ~ e s *ai: a a :ays L. m it %Ils Drarv Leptocera.ae PL 5vJia13' Pelf e--is 8&arraisters C era !ea r e- * ' a'a + Y e:tes t Isntala M,3v m g e.airicius)
Z iv-t nea (say s
- 1. fia74 '-avs*
(. t e r s "uv - t's - *:r-ies e Petitec=-is treers Cars 'er* - . ,, i t? . nears CalopteUnidae ' t a t :e9 *e'- '*8 a
.al'er) l'e1.te,L1.ed areric ar.g iTatri;ivs) "e-t!.s sp.
(oenag r io nidae Lepidoptera Arr.13 anfralis day) Pyralidae
- 6. rests O .: ten) Pr"- -4 .p.
. 4. translata Otages. Para. r. -1s sp. itull s- a c ivile Fages: Coleoptera L. e-svla9s *Hages, P.Allpl144e
'sr b'nre vert ic alls (iev e alte!:s sp.
Fleceptera Felta: *es /xferi n tli t ($ay) Pteronarc LJae Dyt1sc14 e Pterm areve sp. Cerelat.s sp. Taestcpterynadae Lacee- 1;2s sp. e rae% +rers fascista sLar eitter) Cyriniese Tsenterteryx sp. Dises ee d f sc.* Sr M4
!srmvridae 2. ag,I,u F4:a:ts a-
.evvr.n deloss Richer Certt.s sp.
Capniidae hydrepn11 t:4e Allerannia sp. Per ,3 a:.*ta hs LeC4=*.e PerlidAe IrWi*e".s .attra. 3 TL**4 h s (Say) Ac reneuria sp.
- I. r.atzt;r .*t serm:::
Peritsta plac19e eEa4ez Psephenscae Periodidae Ps e?'e r.s 6e K ' sieJave footerla tillfeest s (f ar - Elmidae Meetptera Ascer >--- v arie r a t 4 . err.ar e Cortmidae w i a--;a -r .:::::
- m;;=te . e Site's 11termta f 5aya 2. vitta.a . N.ste.:.ar Trtcwncort=a e uav)
- v -'-- - - a r.atrar:' .ar
%tonec tidae e- t i n e -m e - -:r Irevas vte,ec t s unblara f at
% 11. : : . S la: + s .'e . tes Belos tomat adae Pr~v e s t a e ' ei s.s .m'. .:a s Belott *a sp. Stene9 ; re. ra.a ra.:.arszs
%epidae kanatra gl4Lg lierricts-!chaef f er
- 1. a r -1 i .s ta s t.4.s sv Chrysotamiacae Ca t as toc aridae N .ac ia sp.
Celu toce*is cculat.s (Tabricius) Dipters Cerridae Tipulidae f.it,yh arrea*icell t s Parshley Acteca sp. fg . conformts 4L?ilers Pr at. J sp.
et roMee g hespert .s . Mer *tMla sp.
*%eu utpates rt;rt SerCroth Psychodicae Yeltidae Perte: a sp.
ic revelia a,crice J GSler) Ps c'c e sp.
*harovelia e thier Tel .i- se- 2s sp.
Pusoveltidae Culicidae
etovelia r 11santi ^.htte tt.ie,1 e s* ass paige: e
$aldidae Chaotwridae Pentacora litate (Say) ChaA r.s ns:!f e', !se)
Saldala sp. Chironomicae
?'esaloptere Tanypodinae Stalidae Ta m s ap.
5talis sp. Procla**_s sp. Corydatidae Ps ec t- 1--+ s s p. ferydalus cernutas fL1=:4eus) Coele rn ?m s r ,-i :._s .Cce,.111ett ) Neuroptera S. sea-larte e;ses. 51svridae Ak l a' c e- t a -4 -
- e.a".ew )
Cit.nacis aretarts (dagen) 6. nr. -- s- nr s !ac a a.1d Seck Trichoptera S te e a n_ a grc .:p sp. Psycheviidae Die =es a n,s e Psvehee via flaytda Fagea Of a e?e sp. Po!)c ent ropod ida e Orthociacitrae Neureci f 9 sis sp. ?rillia sp. Po l r en t en~2, cluere.s Iaaen Cric 3t- n M:W- s gr:;p sp. Hydropsychidae E. es'.eere:s g :.y sp. Che-uteeevche e s--"l a tass Crice : s s;p. Myd & sychs aeratt fans Inte*e,-te!1a s73. B. bilita group sp. Feter- -is' H. Tr994 Hates 'af us M Jaet.her W!' cisa as e ;- 'a: :s) sp. M. Pale 4ta ! laten o-t' a; s --
.y sp.
'.st raami r arell u lacas Pari e sp
- 3. sbritu:n 4iageo Clossoso utidae e see--
-t e c.p .
;i .
F ::.a s o. Pretr etta eslina (7.:sse ger.;s c.r. -i - 12 ' -, u ffer 1565 158
110 Table 3.1 7 seat tra ed. Arthropoda - c ont Laued 41..s< a lasetta coattaueJ M trepoda Dipters - contim.ej 'aaoms tortw ra Chare,cuidae a contLiued g 1*iys t Jae Chironomisas h sp. chi ran t duer.s Johannsen Ly mastese t -n* c' + - rms ar. t i e r t r.a 4wnes t rataea S.=llis Say L. ar. m tJohanaseu Plawre scae re-fe - t :Meevwis wirerat s ;etterstedt evri s t as rarams t asy, ricrete- en m fe=tus (say s Pellsc a tri .1vts 'Says
- 2. rerw a.s tataegers Anc yt tda teh H r-v-=:n nr. tendeas (Fabric ius) terrissfa rtwlaris (;ays c1va*-tea
- es sp. 1. taria (says emmt se mia ar. a echens Townes ?.esogestropoea Parse m n s sp. Pleutw e rida e Parec i s t'*e; J sp. Coci#ade,it'Ilgite # 4 1108 Perste-ffree sp. . r t ro : 1 c a r t tu t a I f,r*Jf41E re l Paenc-gect-a (f errentia) ar. ettitens (Johannasal valvatadae Mae,r es ec t ra cr thles s sp. t af rata trica-inat a rJays Petr-et t i m t all as group sp. HydreDLtdae
- 1. helterst e (Coquillet) t.-itet t a ILsps a (Say)
- 2. or, a t '.uense (Malloch) 5 Lt 7.a tent aculst a ("Lasavust Z scatact_s tschrank) Vistparteas ste mc-tr e s sp. Ca v eic*a deelta (Says
- t le t~ -ir- r u s sp. ?elecneda eeetac-et arn a r.r. est ews (Johannsen) Euleraitttiras hia Tawt a s us nr. h.c < ! evi asblette Unionidae faivem-sus sp;. Avd res cata' acta ( a?)
Cerstopegastdae ttil?tta ecm tsu ta (Laghtfost) Pal m rta group sp. 1..t rst11s sp. 51sn411tda e Eeterodonta T Lw11/3 (?tilo?ta) vittat a Zetterstedt 5phaertidas Tabasadae Ptsifim sp. O rvseps sp. !Maer. r1 sp. Empididae I'cwrMrmia so. Dolichopedit.ae Ephydridae Nstidae fs17te op. EL123 sp. Q
~
f \ 7Mi ,[ A[ i . [\ I (( D D '
"1 evJ ML L e~uW o O
1565 159 e
O ,n 111 0 f, rC ( Dm s aioer p f:o 'UP'io:'Lx>(q
.i I O 3 ( pU db bCb d ff Table 3.2 1 Nu-bers and nilitarans of bio ass, . ir.,), of benthlc organisms per Po ar grah (529 cE) at station n'-AQ1 1A1,
.$pril 1976. !< ashes laJicate species :wt present or ns weight Aasgra e =ade,
~
flate o Apral 20 April T ir:e 0935 ,09:0 Air rep. Ici 13.5
'.'at e r f e' p. (( r 25.5 8.0 20.0 Dissol ed m ygen .ppe) 9.6 8.4 PH 7.6 8.0 Secchi Msc (cns 43.2 127.0
- River Stage (f t) 6.6 4.7 fubstrate Sand, Coal, Nd, retritus fand, Coal, 2etritus N d ecst{ cite A q r 9 e i ( 3
.ir ertinea .
1( f li.# 2 .- p - 1(.) *
- h itoda - -
1(.) Enc hyt rae idae 1 (. ) 1(.) 2 (- ) 1 (-9 1(-) 1(-) - 1(-) 1(-) - - - his b.eesescri
- I f. , 1(-) -
3(-) - .- - -
- 3. e l t L i s . - - - 3(-p 1(.) 4(-) .
- 3. va r t e n - -
1(.s 1(-) . - - 1(. ) 2 ancN ira Etib:1 - - - - I I.). 6 8 1(1.0) . 1(3.5) t i nx - * ' v e c13,3reten ema 2(-> . 3(.) 1(-) 10(5. ir s 1G(5.1) . . L. hote ei teri . 1(-) 2(-) :(., . . 12(7.0) 32(14.6) L. u d e > <- t .sm s . - 1( . . - - - - t i-nceri t. s spp. 4(.) 10(.) 17(.s Palosenlev -r el etoe :s 1(-) 1(-) 6( i 19(1!.2) 29(14.9) 33(22.1) 2)(17.8) i(-) 1( j . . - Tub t iev. t:%[few . . g(.) 1(-) - tr:. . tub./ cap. chaetae*
- 1(-) 1(.) 2(.) - -
3(-) $(3.6) Lurbriculidae . . . 1( ) - - g(.) - ltegadrile . - . - Decctis sp. - . 1(-) 1(-) II.) . - - - - Psychefi sp. pupa - . - 1(0.7) - - - Praciadias sp. - - 1(-) . . . . - rricot**u9 spp. - - 1(*) . - - . . C r ic eto~?< spp. pupa - . 2(-) - . - - . P.ir=-etet.xnems sp. . - 1( ) . - - . Chiron9 us deentis - - . . .- Phte9<'?**ctri nr. c'effe9s - - - - 1(.) 1(.) - Polynedilt- La Qa; group sp. - - . - 1(.) . . 4(-) Ferrisota spp. 1(-) . . . 1(.) Cont.+asts virrt,fea a'17.2) - 6(82.3) 1(9.1) 7(103.2) . 3(8.6) - Pi n t o t-:9 sp. . 17(-) 16(-) 12(-) Wh s e r t 2, sp. 5 (-) 1*(-) 4(-) - 4(5.0) 12(-) 3(.) - 2(-) 1(-) 3(-) + Imature tub tf ic ia with capt111f err. chaetae. 1565 160
O GQ l; r \ U $) l k l} fn , m Tat!e 3.2 2
%sters and milligrams of bloc. ass, a (eg), of beet?.le organte-s per Ponar grab (52 7 c 2) at dtation TM*AQI-1A1, yay 14*6. Dashes indicate species not present or .io weight reasure ent e.aJa. . ate a May la May 2; ., 1009 1015 41r Te=p. (C) 7.A 19.0 .ater Te P. (C) 11.8 20.0 21sutved oxygen (ppm) 9.0 2.0 e 7.t :;A Jeccht 21sc (cm)
- 66.0 61.9 1* er stage (ft) 4.9 .6 rhetrate hd, sa.*. , 041. sore mtritu. !bd. :;and, toal, se Neritus s.- !:at, A ? r 9 ; n e i w rtinea - . . - - -
1(0.56 14-.
.e.atoda 12 (1. (. ) 7'O.5) 7(0.3) 7(0.7) (.) 4(.) 2(-) -
s:_.atetts -ere's P* - . P - . - -
~' net rsster etae5ae.us . - - -
2(-) - . 5(-s is.11 t etseeert 12(0.3) - . - - - . . 2 3li. .nl.1 115(2.7) 153(2.7) 231(5.4) 13S(3.2) 635(16.65 5e(1.2) 205(5.2) 3 2 '. ( e .; , J. v11-s5tlis - 21(0.;) 2a(0.6) 10(0.2) 59 '!.i . - 11(0.3) . M i ' .z i s s e rve n t i na - - . " 3 C f.'. 7 ) - . .
? tinsit it.is.1 -
35(0.6) . - 3(*) . . 15(0.L. 2-s .si,.x .e.e-met 1(-) - 1(0.6) . - . - .
- --t lu s r e-e l e tml - - . . -
- 8(2.3) .
~'- .'*?ttus eta 9aredelanus . - . .
20(2.6i . . .
.. W i eistert 32(7.7) 5;(3.1) 570.7) 10(1.5) 01(5.2) 11(2.2s 21(4.2) 65(13.r.
1 deWe-tanus - 1 (2.11 . . . . . .
! r-'-tius spp. 128(30.9) 2(12.3% 12s(18.0) 121(13.6) 133a23.7, 69(13.9) 127(25.1) 43(9.2 N =c !cx atitteetosus 2(4.0) - .
2(0.7) . . ;go,9) 3 g t, ,, h te ifex 5(0.9) 13(2.6) 8(2.4) . .;(9.2, . s(2.3) 17(3.1
-z. tsb./c ap. chaetae** 18(3.3) 21(;.2) 32(9.5) -
52(10.Se 13(-) 31(s 9) 17(3.-
#egafrile 2(.) 1 ( . ', - - - - . -
.!-5'etta linesta 1(1.9) . - - - . .
<-feita sp. - - - . . .
1(.) - r/tracarina 1(.) 1(-) . . - - - . s+ ' s e --.m i s - - - - . - 1(o,;) . w ar:s fasciscus - 1(.) 1(-) . 4(0.5) 3(0.4) sv1.1) 4(1.1,
- e. at:: sve 5e sp. 1(-) 3 (1.0 p 1(0.8) 4(2.2) . - - . "---- s ve *e r5s t e rs ta . - -
1(1.1) . - - .
-r -se-32s sp. . - . .
1(.) - . -
- e. e.-is spp. l(-) - . . . - - -
r- - 111 s so. - - - - 3(2.7) 2(-) 2( ) 2(..
.ir + a sp. .
2 (- ) . . . . . -
'-t ' M us spp. -
5(0.1) 1(-) 3(0.3) - 1(-) . .
.*t. !:rls spp. pupa -
1(-> 2(-) . - - . - ae-lette sp. A 1(-) . . . . - . .
'" claitus (S orthoclaifus) sp. - - .
3(0.3) - . . . r-' xlai.!s.1 (Ortuelailus) sp. 1(-) i(0.2) 18(0.5) 9(0.8) . 2(-) 3(-) .
"?? ictaflus (Arthocladius) rp. pupa - - -
2(-) . 1(.) . .
* .i mc l a ilu s sp. .
U O.1) 1(-) - . - . 1(.y [:m-misdecor*;s . - 2(.) - 3(.) 5 (- ) 2 (-) 2(.;
. N-!* pups 1(.) . . . - - . .
H -t-fa m e! a sp. - 1(.3 . . - - - -
** W 3*ectra nr. obeitems . . . - 4(0.3, 1(.) 3 (. ) 2(.)
+:itum fallsx pupa .
!(-) . . - . . -
- 2. : . tiltree,se 3(-) -
12(0.3) . - - - - 24 rtarsini pupa .
! (- ) - - - - - .
t- rsus sp. t a group sp. t(-) . . - 1(.) - - t(.)
- s. : : sp. . -
1(.) - - . . . e-t- Hsis virrinica 2(9.9) - . - 1(20,3) . - 1(33,7, s p. 1(.) 2(.) - 7(3.0) . 2 (1.0) 2(2.0
-u-M s? .
2(-) 1( ) . . - 1(.) 3(5.2.
".4 = vt Available. * '. .ar.t tration not pos sible: eenotes orgsnise prsse.t. *
- mature tubific td with capilliform t haetae.
1565 161
^
0 D a 113 ML 4'f iLb m,l
- l go .\ j$ i,n,i isif
? ,
table 3.2 3
*:st ' ers anJ mal!! ara s of t i-n s. frg). of benthic organie s per Ponar irat '!D c ,) er ' tat. : -"-Ma l 1 A1 Ju nt l'#7%. Past.ee incicate species m?t presert er es weight easurement =c a.
Is.s t e 1 J...e 15 J :t e fire 'se 27 075.' Air It 7. (C b 22.0 22.5 L ter rsep. 't
- l 's .'s 22.5 e
*Ji.sulved acysttn (pp.,
's . 2 7 's Pit}}