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SPAWNING  ESCAPEMENT 

OF  OKANOGAN  RIVER  BLUEBACK 

SALMON  (O.nerka),  1957 


Marine  Biological  Laboratory 

'     19:;9 

WOODS  HOLE,  MASS. 


SPECIAL  SCIENTIFIC  REPORT- FISHERIES  No.  275 


UNITED  STATES  DEPARTMENT  OF  THE  INTERIOR 
FISH  AND  WILDLIFE  SERVICE 


EXPLANATORY   NOTE 

The  series  embodies  results  of  investigations,  usually  of  restricted 
scope,  intended  to  aid  or  direct  management  or  utilization  practices  and  as 
guides  for  administrative  or  legislative  action.    It  is  issued  in  limited  quantities 
for  official  use  of  Federal,  State  or  cooperating  agencies  and  in  processed  form 
for  economy  and  to  avoid  delay  in  publication . 


United  States  Depeurtanent  of  the  Interior,  Fred  A.  Seaton,  Secretary 
Fleh  and  Wildlife  Service,  Amie  J.  Suomela,  Commissioner 


SPAWNING  ESCAPEMENT  OF  OKANOGAN  RIVER 
BLUEBACK  SAIMON  (ONCORHYNCHUS  NERKA) ,  1957 


by 

Donovan  R.  Crsuidock 
Fishery  Research  Biologist 


Special  Scientific  Report--Fisheries  No.  275 


Washington,  D.  C 
December  1958 


The  Library  of  Congress  catalogue  card  for  this  publication 
is   as  follows: 


Craddock,  Donovan  R 

Spawiiiiifr  es-capemcnt  of  Okanogan  River  blueback  salmon 
(Oncorhynchus  nerka)  1957.  Washington,  U.  S.  Dept.  of 
tlio  Interior,  Fish  and  Wildlife  Service,  1958. 

8  p.  (iiagrs.,  tables.  27  cui.  ( Special  sclentiac  report— fisheries, 
no.  275) 

Bibliography:  p.  7. 

1.  Salmon.  i.  Title.  (Series:  U.  S.  Fish  and  Wildlife  Serv- 
ice.   Special  scientific  report :  fisheries,  no.  275) 

[SH11.A335    no.  275]  Int  59-19 


U.  S.  Dept.  of  the  Interior.     Library 

for  Library  of  Congress 


The  Fish  and  Wildlife  Service  series,  Special  Scientific 
Report — Fisheries,  is  catalogued  as  follows: 


U.  S.    Fish  and  Wildlife  Service. 

Special  scientific  report :  fisheries,   no.  1- 
(Washington,  1949- 

no.     iUus.,  maps,  diagrs.    27  era. 

Supersedes  In  part  the  Service's  Special  scientific  report. 


1.  Fisheries — Research. 
SH11.A335  639.2072  59-60217 

Library  of  Congress 


ABSTRACT 


The  blueback  salmou  spawning  area  of  the  Okanogan  River 
has  been  surveyed  extensively  each  yeeir  since  the  start  of  a 
Canadian  flood-control  project  in  1951.  The  spawning  populations 
have  been  estimated  and  their  distribution  above  Rock  Island  Dam 
detezmined.  The  large  niiober  of  fish  unaccoxmted  for  may  be 
partially  attributed  to  mortalities  caused  by  the  high  water 
temperatures  existing  in  the  Okanogem  River  prior  to  spawning. 

The  age,  length,  eind  sex  compositions  of  the  1957  Okanogan 
River  spawning  escapement  were  determined  from  samples  collected  on 
the  spawning  grounds.  Althoiigh  seme  delay  in  passage  occurred  at 
the  thirteen  newly  completed  drop  structures,  completeness  of  spawn- 
ing was  not  abnonoally  low. 

The  occurrence  of  large  numbers  of  33 's  ^  *^  spawning 
population  seems  to  be  peculiar  to  the  Okanogan  River. 

The  distribution  of  fish  on  the  spawning  grounds  has  not 
changed  appreciably  since  1952. 


TABLE  OF  CONTENTS 

Page 

Suirveys 1 

Spawning  escapement  1 

Water  temperatiire 1 

Composition  of  escapement k 

Spawning  success k 

OccvoTrence  of  32'" 7 

Distribution 7 

Experimental  channel 7 

Svmnary  and  discussion 7 

Literature  cited 7 


SPAWNING  ESCAPEMENT  OF  OKANOGAN  RIVER 
BLUEBACK  SAI/<ON  (ONCORHYNCHUS  NERKA) ,  1957 


The  encroachment  of  civilization  has 
greatly  restricted  the  spawning  migrations 
of  the  Columbia  River  blueback  salmon. 
The  Osoyoos,  Wenatchee,  and  Redfish  Lake 
systems  are  the  only  spawning  and  rearing 
areas  of  importance  remaining  available  to 
this  valuable  species  of  Columbia  River 
S6uLmon> 

The  spawning  area  of  the  Okanogan, 
which  is  the  most  important  of  the  three 
systems,  has  been  channelized  recently  in 
connection  with  a  Canadian  flood-control 
project.  This  channelization  necessitated 
construction  of  13  drop  structures  (small 
dams  with  3  feet  of  head)  which  the  salmon 
must  ascend  on  their  migration  from  Lake 
Osoyoos  to  the  spawning  area.  Annueil  sur- 
veys have  been  made  to  detenaine  the  im- 
mediate effect  of  the  flood-control  work 
on  the  salmon  and  to  see  that  all  steps 
necessary  for  their  protection  are  taken. 
The  long-range  effect  of  this  project  on 
the  Okanogan  blueback  runs  will  not  be 
known  for  several  years. 


SURVEYS 

Blueback  spawning  activities  in  the 
Okanogan  have  been  surveyed  extensively 
each  year  since  the  flood-control  project 
started  in  1951.  Five  surveys  were  made 
this  season  in  much  the  same  manner  as  in 
previous  years.  The  1957  surveys  were  of 
particular  interest  because  for  the  first 
time  the  fish  have  had  to  ascend  the  new 
channel  with  its  13  drop  structures.  Since 
a  partial  block  existed  at  drop  structure 
No.  2  during  the  last  half  of  September, 
special  attention  was  given  to  the  spawn- 
ing success  of  the  migrants.  This  delay 
plus  the  possibility  of  other  delays  could 
cause  the  fish  to  arrive  at  the  spawning 
area  too  late  and  too  weeik  for  successful 
spawning. 

The  section  designations  used  in 
pluvious  years  were  followed  closely.  These 
sections  and  the  location  of  the  drop 
structures  ajre  depicted  in  figure  1  (page 
2).  Conditions  for  observing  the  spawners 
were  very  good  except  on  October  22,  when 
wind  and  snow  made  observations  difficult. 


The  area  from  the  Southern  Okanogan  Lands 
Project  Dam  to  drop  structure  No.  13  was 
surveyed  by  rubber  boat,  and  the  area  from 
drop  structure  No.  13  to  Lake  Osoyoos  was 
checked  from  the  dike  paralleling  the  river. 
A  few  spawning  fish  were  observed  near  drop 
structures  No.  6  and  No.  13,  but  the  spawn- 
ing below  No.  13  was  of  little  importance. 


SPAWNING  ESCAPEMENT 

Table  1  presents  the  actual  counts 
made  on  the  various  surveys  and  table  2 
shows  the  spawning  population  estimate 
derived  by  the  "Factor  5"  method.  This 
method  (Gangmark  and  Fulton  1952)  has  been 
used  on  the  Okanogan  for  several  yeeirs. 
Although  we  are  convinced  that  it  gives  a 
consistently  low  estimate,  we  feel  that  it 
serves  as  a  reliable  index  of  the  magnitude 
of  the  spawning  population. 

The  1957  count  of  blueback  through 
the  fishways  at  Rock  Island  dam  was  71,261. 
Of  these,  28,231  were  counted  at  Tumwater 
Dam  on  the  Wenatchee  River,  8ll  were  taken 
by  "up  river"  hatcheries  and  miscellaneous 
samples,  and  an  estimated  3>017  were  taken 
by  the  Okanogan  Indian  fishery.  The 
"Factor  5"  estimate  of  25,350  for  the 
Okanogan  spawning  population  leaves  13,919 
fish  or  19.5  percent  of  the  Rock  Island 
blueback  count  unaccounted  for.  Table  3 
is  a  record  of  the  distribution  of  blue- 
back  above  Rock  Island  obtained  by  using 
"Factor  5"  estimates  for  the  Okanogan. 
The  increasing  number  of  fish  accounted 
for  in  recent  years  is  probably  due  to 
improved  siirvey  techniques  euid  accurate 
counts  obtained  at  Tumwater  Dam. 


WATER  TEMPERAIURE 

Although  it  has  not  been  proved, 
many  of  the  fish  unaccounted  for  may  have 
succumbed  to  the  effects  of  the  high 
temperatures  encountered  in  the  Okanogan 
during  the  migration  period  (fig.  2).  For 
more  than  2-1/2  months  during  July,  August, 
and  September,  the  river  temperature  was 
well  above  the  65 "F.  level.  These  high 
temperatures  are  common  since  the  four 


S.  O.L.R   Dom 
A 


\Voseou)(   Lake 
SO.L.P  Dom 


CANADA 
U.S.A. 

OROVILLE  L-/zoselDam 
Area  Mop \^ 


-   Section     designotions 
=  Verticol   drop  structure 


Figure   I.        DIAGRAM; 
CHANNELlZATIOr 
SPAWNING     GROUNDS     OF     THE     OKANOGAN'R. 


Tabl«  1.— Spawning  ground  surveys,  Okanogan  River,  1957 


Section 

Sept. 
25 

Oct. 

1 

Oct. 
8 

Oct. 
15 

Oct. 
22 

Total 
live 

Total 
dead 

Live 

Dead 

Uve 

Dead 

Live 

Dead 

Live 

Dead 

Live 

Dead 

838 

A 

129 

155 

285 

221 

1 

48 

1 

B 

272 

491 

1773 

2 

1212 

50 

463 

112 

4?n 

164 

C 

173 

923 

1879 

3 

131*3 

1*7 

320 

198 

4638 

248 

D 

115 

530 

570 

1286 

1*4 

31*3 

283 

2844 

327 

E-H 

252 

759 

k 

2803 

12 

1551 

384 

436 

858 

5863 

1258 

H-K 

hk 

299 

1179 

17 

1076 

l^h 

248 

397 

2784 

568 

K-13 

50 

10 

30 

90 

Total 

985 

3207 

k 

8499 

3^* 

6719 

680 

1858 

1848 

21,268 

2,566 

Table  2. — "Factor  5"  estimates  of  Okanogan  spawning  population,  1957 


Section 


E-H 


H-K 


K-M 


Survey 
date  y 


10/1 
10/8 
10/15 
10/22 

10/1 
10/8 
10/15 
10/22 

10/1 
10/8 
10/15 
10/22 

10/1 
10/8 
10/15 
10/22 

10/1 
10/8 
10/15 
10/22 

10/1 
10/8 
10/15 
10/22 

10/1 
10/8 

10/15 
10/22 


Count 


155 

285 

221 

48 

491 
1773 

1212 

463 

923 
1879 
1343 

320 

530 
570 

1286 
31*3 

759 
2803 
1551 

436 

299 
1179 
1076 

248 

50 

10 

30 

0 


Average 


Am. 


177 


985 


1116 


682 


1387 


701 


22 


885 


4925 


5580 


3410 


6935 


3505 


110 


Estiaate : 


25,350 


1/  The  Survey  of  9/25  wa*  ellninated  since  spawning  was  not  actually 
in  progress. 


large  leikes  In  the  Okanogem  chain  pemit 
great  surface  heating. 

Figure  2  also  Illustrates  the  varia- 
tion In  temperature,  62'  to  Wf.,  during 
the  period  of  spawning-  The  peak  of  spawn- 
ing occurred  at  a  temperature  of  approxi- 
mately 53'F. 


ratios  in  the  two  age  classes  as  well  as 
the  age -class  composition  of  the  entire 
sample.  The  32 's  made  up  30  percent  of 
the  sample  and  had  a  sex  ratio  of  1  male 
to  0.514-  females  while  the  k^'s  made  up 
70  percent  of  the  sample  and  had  a  sex 
ratio  of  1  male  to  I.62  females. 


CC»1P0SITI0N  OF  ESCAPEMENT 

A  sample  of  695  fish  was  measured  on 
the  Okanogan  spawning  grounds.  The  length 
frequency  curve,  figure  3>  clearly  indicates 
the  occurrence  of  the  two  age  classes  com- 
prising the  spawning  population.  Exami- 
nation of  the  otoliths  from  79  of  these 
fish  disclosed  that  the  dividing  line 
between  the  32 's  and  42's  lies  between 
18  inches  and  iS-l/l*-  inches  for  females 
and  between  I8-I/2  inches  and   18-3/^  Inches 
for  males  (table  h).     This  table  also 
demonstrates  the  divergence  of  the  sex 


SPAWNING  SUCCESS 

Table  5  is  a  record  of  a  much  larger 
sample  examined  for  sex  and  for  spawning 
success.  A  total  of  2,046  fish  were  sexed, 
and  the  females  were  examined  for  complete- 
ness of  spawning.  The  overall  sex  ratio 
of  medes  to  females  in  this  sample  was  1: 
1.3^,  and  92  percent  of  the  females  were 
canpletely  spawned.   In  1955  and  1956  the 
percentages  of  completely  spawned  fish 
were  9'*  and  95  respectively,  which  indi- 
cates that  the  delays  encountered  by  the 
1957  spawners  did  not  materially  affect 
their  spawning  success. 


Table  3* -'Distribution  of  blueback  salmon  above  Rock  Island  dam 


Year 

Okanogan 

factor 

5 

Wenatchee 
counts  1/ 

Entiat  & 

Methow 

Hatchery 

Indian 
catch 

Total 
accounted 
for 

R.I. 
count 

^  of  R.   I. 

count 
accounted  for 

I9U7 

18,125 

38,230 

135 

5,000 

61,1+90 

79,831+ 

77.02 

19kQ 

35,885 

38,205 

90 

5,000 

79,180 

81+,627 

93.56 

19^*9 

310 

3,880 

- 

500 

l+,690 

18,682 

25.10 

1950 

- 

- 

- 

2,500 

- 

50,059 

- 

1951 

12,21+0 

17, '^95 

200 

5,000 

3'*,935 

102,721+ 

31+.  01 

1952 

25,000 

19,200 

1,000 

3,000 

1+8,200 

113,703 

1+2.39 

1953 

3lt,260 

15,000 

3,203 

^+,533 

56,996 

152,013 

37  A9 

1951* 

13,206 

25,000 

100 

3,9^^ 

1+2,252 

91,181+ 

1^.33 

1955 

'♦7,930 

50,000 

1,105 

4,626 

103,661 

155,782 

66.51+ 

1956 

39,256 

25,518 

203 

3,598 

68,575 

92,209 

71+.  37 

1957 

25,350 

28,231 

811 

3,017 

57,1*09 

71,261 

80.56 

1/  Factor  5  estimates  through  '52  and  counts  at  Tumwater  Dam  thereafter. 


- 

FIGURE  2 

AVERAGE    DAILY    TEMPERATURE 
OKANOGAN     RIVER— 1957 

80 

_ 

75 

" 

>\' 

,1 

ZOSEL    DAM 

f^^ 

' 

1  ,                   /      .,'. 

70 

X 

leo 

X 

< 

If 

"•MA'  /  / 

""^ 

CO 

UJ50 
liJ 

q: 

- 

^^ 

IU45 

^                  \/                                     ^  ^^ 

SPAWNING                                                VVr^ 

40 

- 

^K^ 

35 

1 

1    1    1 

1       1      1      1      1      1 

1         I       1        1        1        1       1         1        1       1        1       1       I         1        1        1        1       1        1         II 

5      10     IS    20    25     0      5      10     15    20    c'O      0      5      10     15    2C'    25     0       5     10     15    20   25 

JULY  AUGUST  SEPTEMBER  OCTOBER 


5      10     15    20    25      0      5 

NOVEMBER 


75 


CO 

u. 

li. 
o 

LlI 

m 


25 


FIGURE  3    LENGTH    FREQUENCY   OF    BLUEBACK 
SALMON,  OKANOGAN    RIVER,   1957 


635 COMPOSITE 

324 MALE 

37  I FEMALE 


1475  1550  1625  170  1775  1850  1925  200  2075  2150  22  25  230 

FORK    LENGTH-MIDPOINT    OF     1/2"  INTERVALS 


Table  k. — Age-group  breakdown  as  deteimined  from  otolith  study, 

Okanogaui  blueback,  1957' 


Age 
group 

Males 
No .  Length 

Females 
No.  Length   Total 

Sex  ratio 
M  :  F 

Percent 
females 

i 

of  total 
sample 

32 
U2 

139  <18-3A" 
185  18-3/4" > 

70  <  18-1/4"  209 
301   18-1/4 "2. 486 

1.00:0.54 
1.00:1.62 

35 
62 

30 

70 

Total 

324 

371          695 

1.00:1.14 

53 

100 

Table  5.— Sex  ratio  euid  spawning  success  of  Okanogan  blueback, 

1957. 


Survey- 

Total 
dead 

Dead 
exam. 

Sex 

Sex  ratio 
M  :  F 

F 

Spawning 
of  fem 
SPO  USP 

success 
ales  1/ 

date 

M   F 

PSP  ^SPO 

Sept.  25 

0 

Oct.  1 

4 

2 

1   1 

1.00:1.00 

50 

1 

Oct.  8 

34 

26 

11  15 

1.00:1.36 

58 

10 

4 

1   67 

Oct.  15 

680 

360 

198  162 

1.00:0.82 

45 

140 

8 

14   86 

Oct.  22 

1848 

1658 

663  995 

1.00:1.50 

60 

929 

29 

37   93 

Total 

2566 

2046 

873  1173 

1.00:1.34 

57 

1079 

41 

53   92 

1/  SPO  -  spawned  out  -  over  751^  Spent. 
USP  -  unspawned  -  less  than  25'3i  Spent. 
PSP  -  partially  spawned  -  25  to  75?i  Spent. 


OCCURRENCE  OF  Sg'^ 


SUMMARY  AND  DISCUSSION 


The  1957  return  of  blueback  was  of 
special  interest  since  the  U^g'^  ^^^^   ^® 
progeny  of  the  1953  escapement  which  was 
one  of  the  largest  in  recent  years.  The 
most  unusual  feature  of  the  1953  r^"i  was 
that  over  86  percent  of  the  Okanogan 
spawners  were  3-y6*r-old  fish  whose  sex 
ratio  of  males  to  females  was  1:0. 75-  1^ 
hulk  of  these  3-year-old  fish  escape  the 
fishery  and  continue  to  the  Okanogan  where 
in  normal  years  they  comprise  about  22 
percent  of  the  spawning  population.  These 
pm^n  fish  seem  to  be  peculiar  to  the 
Okanogan  £uid  su«  seldom  encountered  in  the 
other  two  systems.  Table  6  demonstrates 
the  occurrence  of  3-year-old  Columbia 
River  blueback  for  the  last   7  years. 

The  ccHDparatively  low  return  to  the 
Okanogan  this  year  may  be  peo-tly  attri- 
buted to  the  high  proportion  of  3-year-old 
fish  in  the  1953  run.   Lower  fecundity  and 
possibly  lower  fertility  linked  with  re- 
duced survivfiLL  of  eggs,  fry,  and  finger- 
lings  because  of  their  small  size  may  be 
factors  contributing  to  the  low  return. 


DISTRIHJTION 


The  1957  Rock  Island  count  of  blue- 
back  salmon  was  the  smallest  recorded  since 
1950.  This  decline  was  more  evident  in 
the  Okanogan  than  in  the  Wenatcfaee  system. 
It  has  been  speculated  that  lower  fecundity 
and  poor  survival  of  the  spawn  of  the  32'"* 
that  made  up  86  percent  of  the  Okanogan 
run  in  1953  was  a  factor  in  this  year's 
low  return. 

The  1957  spawning  escapement  to  the 
Okanogan  was  composed  of  30  percent  32 's 
and  70  percent  42's.  The  sex  ratios  of 
the  two  age  cleisses  were  widely  divergent. 
The  32 's  had  35  percent  females  and  the 
U2's  had  62  percent  females. 

Spawning  success  was  good  and  ap- 
parently was  not  affected  by  the  delays 
caused  by  the  drop  structures.  However, 
the  drop  at  many  of  the  structures  was 
considerably  greater  than  anticipated, 
and  some  modification  may  be  necessary  to 
increase  the  ease  of  fish  peissage  at  these 
structures. 

In  gener€il  the  escapement  was  ade- 
quate and  spawning  appeared  to  be  success- 
ful. 


The  distribution  on  the  spawning 
grounds  has  not  changed  appreciably  in  the 
last  5  years.  The  one  exception  is  section 
M-N,  which  for  all  practical  purposes  sup- 
ported no  spawning  this  year  (fig.  h). 
During  the  past  5  years  section  M-N  sup- 
ported an  average  of  only  7  percent  of  the 
spawners. 


LITERATURE  CITED 

GANGMARK,  HAROLD  A. ,  AND  LEONARD  A.  FULTON 
1952.   Status  of  Columbia  River  blue- 

back  runs,  1951.  U.  S.  Fish  and 
Wildlife  Service,  Special  Scien- 
tific Report— Fisheries  No.  Jk, 
29  pp. 


EXPERIMENTAL  CHANNEL 


Channel  improvement  work  in  sections 
B  to  D  was  responsible  for  reducing  the 
flow  in  the  experimental  channel  to  a  mere 
fraction  of  normal.  Consequently,  only  88 
fish  were  observed  spawning  in  this  channel 
compared  to  2,600  for  last  year.  This  same 
channel  work  seriously  reduced  the  flow  in 
the  west  channel  causing  an  additional  loss 
of  spawning  area. 


Table  6. — Occurrence  of  3-year-old  Coliunbia  River  blueback  salmon 


Rock  Isl.   dam  counts 


Year 


Total 
run 


Large 
fish 


Small 
fish 


Rock  Isl.   small    fish 
^-Qf      fof 


Total 


totfkL  Rock  Is. 
run    count 


Vfenatchee        ^  of  SgO 
River   Okanogan 
system   River  1/  Okanogan 


1951  201*,  369  89,733 

1952  320,362  104,206 

1953  260,079  99,565 
195**  178,581  76, 7  W 

1955  244,879  145,461 

1956  202,240  74,563 

1957  156,000-^  63,733 


12,093  101,826  5.9 

9,480  113,686  3.0 

52,182  151,747  20.1 

14,486  91,234  8.1 

7,601  155,062  3.9 

17,880  92,443  8.8 

7,528  71,261  4.8 


11.9 

17,495 

12,230 

- 

8.3 

19,200 

u 

25,000 

- 

34.1 

15,000 

y 

72,000 

86.6 

15.9 

25,000 

49,000 

20.9 

6.2 

51,820 

48,000 

12.7 

19.3 

25,518 

40,000 

24.9 

10.6 

28,231 

25,000 

30.0 

1/  Estimates. 


100 


O      80 
o 


O 


60 


O       40 
UJ 

a. 


20  — 


0*" 


FIGURE    4      DISTRIBUTION    OF     BLUEBACK     SALMON    ON    THE 
OKANOGAN     RIVER      SPAWNING      GROUNDS,  1952-1957 


^AAA 


\ 


1952 


T^T^ 


^i 


\\\v 

k\\\ 


^•> 


1953 


1954 


1955 


1956 


1957 


SECTION 
^A-E 


mni  M-N 


INT .  -DUP .    SEC .  .    WASH .  .    DC.    -j  e  i*  3  • 


MBL   WHOl    '-*;fl>|,|:,,i?n||MI|ill||l 

5  WHSE  01273