I n t e r n a t i o n a l C o u n c i l f o r t h e E x p l o r a t i o n o f t h e Sea
C.M. 1986/H:51
P e a l e g i c F i s h C o m m i t t e e
THE EFFECTS OF A MINIMUM LAMDING S I Z E REGULATION I N THE FISHERY OF NORWEGIAN SPRING-SPAWNING HERRING
J o h a n n e s H a m r e and R e i d a r T o r e s e n I n s t i t u t e o f M a r i n e R e s e a r c h P.O. Box 1 0 7 0 , N-5011 B e r g e n , Norway
A b s t r a c t
E f f e c t s o f m i n i m u m l a n d i n g s i z e ( L C ) i n t h e f i s h e r y o f N o r w e g i a n s p r i n g - s p a w n i n g h e r r i n g h a v e been i n v e s t i g a t e d . T h e h e r r i n g i s a s s u m e d t o be a unit s t o c k , in w h i c h t h e g r o w t h o f i m m a t u r e s d i f f e r s a c c o r d i n g t o t h e d i s t r i b u t i o n area. T w o i m m a t u r e s t o c k c o m p o n e n t s a r e d i s t i n g u i s h e d . O n e d i s t r i b u t e d in N o r w e g i a n c o a s t a l w a t e r s s o u t h o f 7 0 d e g r e e s n o r t h and o n e o f f N o r t h e r n N o r w a y and i n t h e B a r e n t s Sea.
S t o c k and yield per r e c r u i t f o r t w o c o r r e s p o n d i n g s t o c k c o m p o n e n t s w e r e c a l c u l a t e d ( I C E S s t a n d a r d p r o g r a m m e s ) using i n p u t p a r a m e t e r s a s o b s e r v e d i n t h e r e s p e c t i v e areas. T h e w e i g h t in c a t c h by a g e o f i m m a t u r e s i s s e t e q u a l t o t h a t o b s e r v e d i n a u t u m n c a t c h e s ( e x p e c t e d t o be t h e m a i n f i s h i n g s e a s o n o f i m m a t u r e s ) w h e r e a s t h e w e i g h t in c a t c h o f a d u l t s i s t h e a v e r a g e o v e r t h e year. T h e w e i g h t by a g e i n t h e s t o c k e q u a l s o b s e r v e d w e i g h t o f p r e s p a w n e r s . T h e m a t u r i t y o g i v e by c o m p o n e n t i s c a l c u l a t e d by u s i n g t h e l e n g t h d e p e n d e n t m a t u r i n g s c a l e d e s c r i b e d by T o r e s e n ( 1 9 8 6 ) .
T h e a s s e s s m e n t s h o w s t h a t i f t h i s s t o c k i s m a n a g e d at F o a l , t h e r e i s l i t t l e t o g a i n in yield and s t o c k per r e c r u i t by i n t r o d u c i n g a m i f i m u m l a n d i n g s i z e a b o v e 2 0 c m in N o r w e g i a n c o a s t a l w a t e r s ( s o u t h o f 7 0 N ) , w h e r e a s s o m e i n c r e a s e in yield m a y b e o b t a i n e d i n t h e B a r e n t s Sea.
I n t r o d u c t i o n
T h e A t l a n t o - S c a n d i a n H e r r i n g and C a p e l i n W o r k i n g G r o u p c o n s i d e r e d t h e e f f e c t s o f a m i n i m u m l a n d i n g s i z e o f h e r r i n g (1,) at i t s 1 9 8 5 m e e t i n g ( A n o n 1 9 8 6 1 . Based o n an a s s u m e d a v e r a g e g r o w t h p a t t e r n s i m i l a r t o t h a t o b s e r v e d i n t h e s t r o n g y e a r c l a s s e s 1959 and 1 9 6 0 and a n a t u r a l m o r t a l i t y r a t e o f 0.13 for a l l a g e g r o u p s , t h e W o r k i n g G r o u p c a l c u l a t e d s t o c k and yield per r e c r u i t f o r m i n i m u m l a n d i n g s i z e s o f 2 0 c m , 2 5 c m , 27 c m and 3 0 cm. T h e r e s u l t s s h o v e d that s o m e g a i n c o u l d be o b t a i n e d i n t h e p o t e n t i a l yield by i n c r e a s i n g t h e m i n i m u m l a n d i n g s i z e f r o m 2 0 c m t o 2 5 c m a t a n e x p l o i t a t i o n l e v e l o f F O . , , but p r a c t i c a l l y n o g a i n in yield c a n be e x p e c t e d by i n c r e a s i n g 1, a b o v e 25 cm. T h e g r o w t h p a t t e r n and n a t u r a l m o r t a l i t y r a t e o f i m m a t u r e h e r r i n g m a y d i f f e r a c c o r d i n g t o t h e d i s t r i b u t i o n a r e a o f t h e immatures. T h e j u v e n i l e h e r r i n g o f f n o r t h e r n N o r w a y and i n t h e B a r e n t s S e a h a s a s l o w e r g r o w t h r a t e t h a n t h e j u v e n i l e h e r r i n g d i s t r i b u t e d o n t h e N o r w e g i a n c o a s t f u r t h e r t o t h e s o u t h . It i s a l s o r e a s o n a b l e t o a s s u m e t h a t n a t u r a l m o r t a l i t y o f h e r r i n g i s h i g h e r i n t h e B a r e n t s Sea t h a n i n t h e c o a s t a l area d u e t o p r e a d a t i o n by cod. T h e a i m o f t h e p r e s e n t p a p e r i s t o i n v e s t i g a t e t h e e f f e c t s o f m i n i m u m l a n d i n g s i z e s o f h e r r i n g f o r t h e t w o h e r r i n g c o m p o n e n t s s e p a r a t e l y , r e g a r d i n g t h e t w o g r o u p s o f i m m a t u r e s t o b e r e c r u i t s t o o n e u n i t a d u l t stock.
M a t e r i a l and m e t h o d s
S u s t a i n e d yield ( Y ) and c o r r e s p o n d i n g s p a w n i n g s t o c k ( S ) per r e c r u i t h a v e b e e n c a l c u l a t e d by u s i n g t h e I C E S s t a n d a r d p r o g r a m m e s . T h e input p a r a m e t e r s o f w e i g h t by a g e , f i s h i n g p a t t e r n , m a t u r a t i o n o g i v e and n a t u r a l m o r t a l i t y a r e d e t e r m i n e d a s f o l l o w s :
W e i g h t by a g e
T h e w e i g h t s by a g e i n c a t c h and s t o c k by c o m p o n e n t a r e g i v e n i n T a b l e 1 . T h e w e i g h t s i n c a t c h a r e c a l c u l a t e d m e a n w e i g h t in t h e c a t c h e s i n A u g u s t - O c t o b e r f o r h e r r i n g y o u n g e r t h a n 6 y e a r s and m e a n w e i g h t i n t h e c a t c h e s t h r o u g h o u t t h e y e a r f o r f i s h 6 y e a r s o r older. T h e w e i g h t s by a g e i n s t o c k a r e c a l c u l a t e d m e a n w e i g h t by a g e o f s t o c k s a m p l e s f r o m t h e t h e f i r s t t h r e e m o n t h s o f t h e year.
F i s h i n g p a t t e r n
T h e p r o g r a m m e d e t e r m i n e s f i s h i n g p a t t e r n a s r e l a t i v e F by a g e g r o u p s . T h e m i n i m u m l a n d i n g s i z e m a y d e t e r m i n e s t h e f r a c t i o n o f a n a g e g r o u p o f i m m a t u r e s b e i n g r e c r u i t e d t o t h e c a t c h a b l e s t o c k and t h e r e l a t i v e F i s e s t i m a t e d a s t h e proportion o f herring w i t h i n t h e a g e g r o u p s beeing a b o v e t h e 1,
.
T h e f i s h i n g p a t t e r n w i l l t h e r e f o r e d e p e n d o n t h e g r o w t h and i s d i f f e r e n t for t h e t w o s t o c k c o m p o n e n t s . T h e c a l c u l a t e d v a l u e s a r e s h o w n in T a b l e 2.M a t u r i t y o g i v e
T h e p r o g r a m m e c a l c u l a t e s m a t u r e s t o c k a s t h e s u m o f t h e p r o p o r t i o n s o f m a t u r e h e r r i n g in a l l a g e g r o u p s . T o r e s e n ( 1 9 8 6 ) h a s s h o w n t h a t t h e m a t u r i t y o g i v e o f h e r r i n g i s l e n g t h d e p e n d e n t , and t h e r e f o r e d e p e n d s
on t h e g r o w t h r a t e . The p r o p o r t i o n o f mature h e r r i n g by age groups have been e s t i m a t e d as i t ' s p r o p o r t i o n i n t h e spawning s t o c k w h i l e m a t u r i n g ( a t 3 , 4 and 5 y e a r s ) r e l a t i v e t o i t ' s p r o p o r t i o n when f u l l y r e c r u i t e d (mean p r o p . a t 6, 7 and 8 y e a r s ) . These p r o p o r t i o n s v a r i e s a c c o r d i n g t o t h e g r o w t h o f t h e immatures. The i n p u t f i g u r e s o f m a t u r e h e r r i n g o f t h e c o a s t a l component a r e e s t i m a t e d t o 102, 2 5 % , 60% and 90Z f o r t h e age groups 3 t o 6 r e s p e c t i v e l y and 100% above 6 y e a r s . For t h e B a r e n t s Sea component t h e m a t u r i n g i s c a l c u l a t e d t o be d e l a y e d by one y e a r . The f i g u r e s a r e based on v a l u e s f r o m t h e r e s p e c t i v e components o f t h e y e a r c l a s s e s 1959 and 1960.
N a t u r a l m o r t a l i t y
I n accordance w i t h t h e same b a s i c c o n s i d e r a t i o n as d e s c i b e d i n t h e Working Group r e p o r t (Anon. 19861, t h e e f f e c t s o f minimum l a n d i n g s i z e s a r e c a l c u l a t e d f o r t h e f o l l o w i n g v a l u e s o f M:
( 1 ) M = 0.15 f o r a l l ages i n b o t h components;
( 2 ) M1 = M2 = 0.35 and M>2 = 0.15 i n b o t h components and ( 3 ) M1 = M 2 = 0 . 5 0 , M3 = 0.35 and M>g = 0.15 i n The B a r e n t s Sea. The M-values o f 0.35 on j u v e n i l e s i n t h e c o a s t a l component a r e d e r i v e d f r o m a c o u s t i c s t o c k abundance e s t i m a t e s , whereas t h e M-values o f j u v e n i l e h e r r i n g i n t h e B a r e n t s Sea a r e judged a c c o r d i n g t o expected p r e d a t i o n p r e s s u r e
f r o m cod.
S u s t a i n a b l e y i e l d ( Y ) and c o r r e s p o n d i n g spawning s t o c k ( S ) p e r r e c r u i t as one y e a r o l d s ( R 1 ) a r e c a l c u l a t e d as f u n c t i o n o f F f o r 1,-values o f 20 cm, 25 cm, 27 cm (recommended by ACFM) and 30 cm. The r e s u l t s a r e shown i n F i g u r e s 1 t o 5. For t h e coastal. component ( F i g u r e 1 and 2 ) t h e r e i s L i t t l e t o g a i n i n t h e Y / R 1 f o r F - v a l u e s below 0.5 even i f M on immatures s h o u l d be as l o w as 0 . 1 5 . A r e s t r i c t i o n on t h e s m a l l h e r r i n g f i s h e r y i s on t h e o t h e r hand o f much more i m p o r t a n c e f o r t h e r e c r u i t m e n t t o t h e spawning s t o c k . For F = 0.5 an i n c r e a s e i n 1, f r o m 20 t o 27 cm may d o u b l e t h e spawning s t o c k i f M on immature h e r r i n g i s l e s s t h a n 0.35.
For The B a r e n t s Sea component a c o n s i d e r a b l e g a i n i n y i e l d can be e x p e c t e d b y a minimum l a n d i n g s i z e r e g u l a t i o n when t h e e x p l o i t a t i o n i s h i g h . For F = 0.5 t h e g a i n i n Y/R1 i s c a l c u l a t e d t o some 30% if t h e e f f e c t i v e 1, i s i n c r e a s e d f r o m 20 t o 27 cm i n t h e case o f l o w M
( F i g u r e 31, and even i n t h e case o f t h e h i g h e s t M-value ( F i g u r e 5 ) t h e g a i n i n y i e l d i s above 1 5 X . I n a d d i t i o n , t h i s r e g u l a t i o n i s e x p e c t e d t o i n c r e a s e t h e spawning s t o c k by some 300%.
ACFM has as a g u i d L i n e o f e x p l o i t a t i o n r a t e recomended t h a t h e r r i n g s t o c k s s h o u l d p r e f e r a b l y be e x p l o i t e d a t F O , l
.
The e q u i l i b r i u m s t a t e o f s t o c k and y i e l d p e r r e c r u i t f o r t h i s r e f e r e n t p o i n t o f F a r e summarized i n T a b l e 3.The assessment shows t h a t i f t h i s s t o c k i s f i s h e d a t F O . l , t h e r e i s p r a c t i c a l l y n o t h i n g t o g a i n i n y i e l d and s t o c k p e r r e c r u i t by i n t r o d u c i n g a mintmum l a n d i n g s i z e above 20 cm i n Norwegian c o a s t a l w a t e r s ( s o u t h o f 70 N ) , whereas some i n c r e a s e i n y i e l d may be o b t a i n e d i n t h e B a r e n t s Sea p r o v i d e d t h a t t h e M-value on t h e immatures i s b e l o w 0.35.
Norway has introduced a 25 cm minimum landing size of herring fished in her fishery none north o f 6 2 north. Based on the present study it 0
seems fair t o conclude that this is a sufficient restriction on the
small herring fishery in case the overall fishing mortality i s regulated t o a reasonably l o w level. This fishery is regulated by catch quotas and the F is cept below F o a l
.
The propost minimum landing sine by ACFM of 27 cm is therefore regarded as overcautious.Anon. 1986. Atlanto-Scandian Herring and Cagelin Working Group Report, 29 October-1 November 1985. ICES C . M . 1986/Assess:7.
Toresen, R . 1986. Length and age at maturity of Norwegian
Spring-spawning herring for the year-classes 1959-61 and 1973-78. ICES C . M . 1986/H:42.
Table 1 . Input parameters of weight ( g r a m ) in catch and stock by component.
T a b e l 2. Input p a r a m e t e r s o f f i s h i n g p a t t e r n by c o m p o n e n t and m i n i m u m l a n d i n g sizes. T h e f i g u r e s d e n o t e r e l a t i v e Fs by age.
C = c o a s t ' c o m p o n e n t 8 = B a r e n t s S e a c o m p o n e n t
T a b l e 3. Y i e l d and s p a w n i n g s t o c k per r e c r u i t e s t i m a t e s ( g r a m ) at F 0 . 1
C o a s t a l comp. B a r e n t s S e a comp.
FISHING HOTALllY
F i g u r e
1.
C o a s t a l component of Norwegian s p r i n g spawning h e r r i n g . Y i e l d and spawning s t o c k p e r r e c r u i t(SSB) f o r 20 c n , 2 5 cr1,27 c m and 30 cm minimum l a n d i n g s i z e . M=0.15
.I200
1100
. I N 0
,900
. BOO
t 3
- 600 s - 500
B
VI VI
- LOO - 300
FISHING MOTALITY - - -- - --
F i g u r e 2 . C o a s t a l component o f Norwegian s p r i n g spawning h e r r i n g . Y i e l d and spawning s t o c k p e r r e c r u i t
(SSB) f o r 2 0 cm,25 cm,27 cm and 30 cm minimum l a n d i n g s i z e . M1=M2=0.35. M3+=0.15
1100
1030
900
800
700
600
500
LOO
300
200
100
--- .---- -.. .
. . 91 Q2 9 3 0.4 0.5 0,6 0-7 0) 0.9 I D 1,l 12 t3 1.4 IS
FISHING HOTALITY
Figure 3. Barents Sea component of Norwegian spring spawning herring. Yield and spawning stock per recruit
(SSB) for 20 cm,25 cm,27 cm and
30cm minimum landing size. M=0.15
FISHING EDTALITY
Figure
4.Barents Sea component of Norwegian spring spawning herring, Yield and spawning stock per recruit
(SSB) for 20 cm,25 cm,27 cm and 30 cn minimum
landing size. M1=M2=0.35. M3+=0.15
FISHING MOTALlTY