Translation Series No.1211
Translation Series No.1211
Translation Series No.1211
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FISHERIES RESEARCH BOARD OF CANADA<br />
<strong>Translation</strong> <strong>Series</strong> No. 1211<br />
Contributions to the biology and study of the stock<br />
of the Atlantic salmon (Salmo salar L.)<br />
in the Baltic Sea<br />
By . Fritz<br />
• 4e. re<br />
• • '<br />
OEriginal title .Beitraege 2ùr Biologie und. Bestandkundé '<br />
- dee'AtlantisChen LaChses: (Salmi salarL) in der<br />
.0stsee.<br />
•From . :<br />
Berichte der deutschen wissenschaftlichen Kommission<br />
d. Meeresforschung, 18(3/4): 223-379, 1966.<br />
Translated by the <strong>Translation</strong>. Bureaù<br />
. ,<br />
. • Foreign Languages Division'<br />
:Department of the Secretary of State Of Canada -<br />
Fisheries Research Board of Canada<br />
- Biological<br />
Station ..-<br />
St. John's, fld'<br />
r .<br />
• 1969 ,:<br />
.
•<br />
•<br />
TRANSLATED FROM — TRADUCTION DE<br />
CANADA<br />
INTO — EN<br />
German Ehglish -<br />
REFERENCE IN ENGL ISH RÉFÉRENCE EN ANGLAIS<br />
Reports of the .German Scientific Commission for Oceanography<br />
PUBL ISH ER — ÉDIT EUR<br />
Verlag Paul Paxey<br />
PLACE OF PUBLICATION<br />
.LIEU DE PUBLICATION<br />
Hambilrg<br />
DEPARTMENT OF THE SECRETARY OF STATE<br />
TRANSLATION BUREAU<br />
FOREIGN LANGUAGES<br />
DIVISION<br />
AUTHOR — AUTEUR<br />
REQUE,FING DEPARTMENT. Fisheries<br />
MIN ISTERE-CLIENT<br />
DATE OF REQUEST<br />
DATE DE LA DEMANDE No . , 19 68<br />
ZucevY etold<br />
. S05-20 0-10.6 (REV. 2/4s8) '<br />
Fritz Thurow<br />
TIT.LE IN ECNGLISH TITRE ANGLAIS •<br />
YEAR<br />
AN N ÉE<br />
DATE OF PUBLICATION<br />
DATE DE PUBLICATION<br />
VOLUME<br />
ISSUE NO.<br />
• NUMÉRO<br />
1966 XVIII 3/4<br />
SECRÉTARIAT D'ÉTAT<br />
BUREAU DES TRADUCTIONS<br />
PAGE,NUMBERS IN ORIGINAL<br />
NUMEROS DES PAGES DANS<br />
L'ORIGINAL.<br />
223 - 379<br />
NUMBER OF TYPED PAGES<br />
, HOMBRE DE PAG,ES<br />
DACTYLOGRAPHIEES<br />
237<br />
TRANSLATION BUREAU NO. 5660<br />
NOTRE DOSSIER NO<br />
1K 1'1,1 ■<br />
DIVISION DES LANGUES<br />
ÉTRANGÈRES<br />
Contributions to the Biology and Study of the Stock of. the Atlantic Salmon (Salmo salar L.)<br />
in the Baltic Sea<br />
Beitrgge zur Biologie und Bestandskunde des Atlantischen Lachses<br />
betseC<br />
(Salmo saler L.) in der<br />
R5F5RENCE IN FOREIGN I,ANGUAGE (NAME OF BOOK OR PUBLICATION) IN FULL. TRANSLITERATE FOREIGN CHA,RACTERS.<br />
REFERENCE EN LANGUE ETRANGERE (NOM DU LIVRE OU PUBLICATION), AU COMPLET.TRANSCRIRE EN CARACTERES PHONÉTIQUES.<br />
Berichte der deutschen wissenschaftlichen Kommission der MeeresforschUng<br />
BRANCH OR DIVISION<br />
DIRECTION OU-DIVISION Office of the Editor TRANSLATOR (INITIALS) p , p B.<br />
TRADUCTEUR (INITIALES)<br />
PERSON FEQUESTINGDr . A. W. May, y St. John's, Nfld.<br />
DEMANDE PAR<br />
YOUR NUMBER<br />
VQT Ft E DOSSIER N°<br />
769-18-14<br />
DATE COMPLETED<br />
ACHEVE LE<br />
Fehr. 22, 1969<br />
•
sos-2cto—lo-31<br />
DEPARTMENTOFTHESECRETARYOFSTATE<br />
TRANSLATION BUREAU<br />
FOREIGN LANGUAGES DIVISION<br />
CANADA<br />
SECRÉTARIAT D'ÉTAT<br />
BUREAU DES TRADUCTIONS<br />
I. Introduction<br />
3<br />
2. The salmon fishery in the Baltic Sea<br />
2.1. The historic development 10<br />
2.2. The fishing technique • • . .. .. 15<br />
2.2.1. River fishery *16<br />
2.2.2. Shore fishery 16<br />
2.2.3. Pelagic salmon fishery. 17<br />
2.2.3.1. Vessels 17<br />
*2.2.3.2. Fishing gear 11<br />
13 f<br />
DIVISION DES LANGUES ÉTRANGÈRES<br />
VOURNO. DEPARTMENT . oivisioN/smANcH CITY<br />
VOTRE N ° MINISTRE DIVISION/DIRECTION VILLE<br />
769-18-14 Fisheries Office of the Editor ' Ottawa<br />
OUR NO. LANGUAGE TRANSLATOR(MITIALS) DATE<br />
NOTREN ° LANGUE TRADUCTEUR(INITIALES)<br />
5660 'German P.F.B. February 22, 19 6 9<br />
Reprint from Vol. XVIII (1966), Heft 3/4, PP. 223-379<br />
Reports of the German Scientific Commission for Oceanography<br />
CONTRIBUTIONS TO THE BIOLOGY AND<br />
STUDY OF THE STOCK OF THE<br />
ATLANTIC SALMON ( Salmo salar L.)<br />
IN THE BALTIb SEA<br />
By Fritz Thurow<br />
Federal Research Institution for Fishery<br />
Institute for Shore- and Inland-Fishery<br />
Cont.ents
2.3. The extent of the pelagic salmon fishery<br />
2.3.1. The fishing grounds<br />
2.3.2. The fishing season<br />
2.3.3. The yield of the stock<br />
24<br />
24<br />
25<br />
26<br />
2.3.3.1. Fishing effort<br />
2.3.3.2. Catch per unit effort<br />
2.3.4. The yields of the salmon fishery<br />
2.3.5. The composition of the catch in the pelagic<br />
27<br />
28<br />
52<br />
fishery<br />
•3. The sexual maturation of the Baltic Sea salmon in the ocean . .<br />
57<br />
60<br />
3.1. The sexual composition of the exploited stock 62<br />
3.2. The condition of the gonads 64<br />
3.2.1. The ovary 66<br />
3.2.2. The maturing of the oocytes<br />
3.2.3. Comparative discussion of the findings about the<br />
7 0<br />
sexual maturation<br />
3.3. The fertility of the salmon<br />
77<br />
84<br />
4. The migrations of the Baltid Sea salmon 87<br />
4.1. The sections of the periodic migration 89<br />
4.1.1. The smolt migration 89<br />
4.1.2. The feeding migration 90<br />
4.1.3. The spawning Migration 95<br />
4.2. Small-scale movements 101<br />
5. Age and growth of the salmon in the main basin of the Baltic Sea 113<br />
5.1. On the terminology of the analyses of age and growth . . . 113<br />
5.1.1. The relation between total length and. fork length . 114<br />
5.1.2. The gutted weight 11 6<br />
5.2. Material and method 118<br />
5.2.1. The arrangement of the scales 119<br />
- 5.2.2. The significance of the sclerite rings for age<br />
determination ............ . . . . . .120<br />
5.3. The age composition of the German catches<br />
5.3.1. The results of the age analyses of January<br />
127<br />
catches<br />
5.3.1.1. The brood year t s sets<br />
5.5.1.2. The sea year classes<br />
5.3.1.3. The salmon with spawning marks<br />
5.3.2. Seasonal .changes in age composition<br />
5.3.3. The age composition of the exploited stock in the<br />
127<br />
128<br />
138<br />
143<br />
149<br />
main basin of the Baltic Sea<br />
5.4. The growth relations<br />
5.4.1. Results of the investigations •<br />
5.4.2. Discussion of the findings<br />
5-4.2.1. The rate of growth •<br />
5.4.2.2. The growth of the smelt of the year 1959.•<br />
5.4.2.3. The effect of the size of smolt on the<br />
1 54<br />
161<br />
161<br />
166<br />
166<br />
168<br />
• growth in the sea<br />
6. The food of the Baltic Sea salmon<br />
173<br />
175<br />
2
• 6.1. Previous investigations 175<br />
6.1.1. The nutrition of the juvenile stages 175<br />
6.1.2. The food in the main basin of the Baltic Sea 177<br />
6.2. Amount and kind of food according to my investigations<br />
1957 -6 4 180<br />
6.3. Differences in the composition of the food 182<br />
6.3.1. Seasonal variation 183<br />
6.3.2. Differences on the fishing grounds 186<br />
6.3.3. Differences depending on the kind of fishing gear . 187<br />
6.3.4. Differences depending on sex 188<br />
6.3.5. Differences in food related to the size or the<br />
salmon 189<br />
6.4. The relation between the behaviour of the prey and the<br />
composition of the food of the salmon 190<br />
6.5. The food consumption of the salmon 191<br />
7. Attempt at a quantitative analysis of the stock in the main<br />
basin of the Baltic Sea 194<br />
7.1. The characterization of the stock 195<br />
7.2. Losses in the exploited stock 197<br />
7.2.1. Total mortality 198<br />
7.2.2. Wasting through fishing and natural mortality . . . 203<br />
7.2.2.1. Results of tagging 203<br />
7.2.2.2. Determination with the aid of the fishing<br />
intensity 205<br />
7.3. Losses in the recruitment phase 211<br />
7.3.1. The natural enemies 211<br />
7.3.2. The mortality un til the beginning of exploitation, . 213<br />
7.4. Models for the stock of salmon in the Baltic Sea 215<br />
Summary 221<br />
References 223<br />
Appendix 230<br />
Introduction<br />
The genUs Salmo belongs together with the genus Oncorhynchus<br />
to the subfamily Salmonininae (Family Salmonidae, Suborder Salmonoidè4<br />
Order Clupeiformes) (L.S.Berg 1958). The Atlantic salmon,'Salmo-salar<br />
occurs in the northern part of the . Altantic Ocean. The distribution reaches<br />
from Cape Cod to the Duero River (Spain) in the south and,from West Green-<br />
land to the Kara River (east of Novaya Zemlya) in the north (G. W. Nikolski .<br />
1957).<br />
1 •<br />
The lifè cycle runs'a very uniform course everyWhere in the .<br />
'entire area of distribution. After a period of ,feeding in the beal:the<br />
.
• maturing salmon seek out the rivers in which they were spawned, in order<br />
to spawn. The females make two- .:10 three-meter long depressions in the<br />
. gravel and shingle bottom in which they deposit their eggs and colter them<br />
afterwards. The duration of the egg development is dependent on the tem-<br />
perature and amounts on an average to about 180 days. After spending from<br />
one to five years in the rivers, the young salmon migrate to the sea,<br />
where they grow very rapidly.<br />
A large number of scientific papers have been written about the<br />
life history of the salmon. J. Bergeron (1962) lists in his bibliography<br />
of the Atlantic salmon for the time from 1800 to about 1960 a total of<br />
1800 references. The scientific research of the salmon received its first<br />
stimulus through the great economic growth of the fishery for the species<br />
[P. 225]<br />
of Oncorhynchus in the Pacific Ocean at about 1860. This led alsoto num-<br />
erous investigations of the Atlantic salmon of the North American coast<br />
of the Atlantic Ocean between 1870 and1880. In Europe a substantial in-<br />
crease in the.scientific activities took place only after 1900 through<br />
eXe ô1 ee Sea .<br />
the founding of the international Council for-Geettnegraphy.<br />
In a partial review of the literature on the Atlantic salmon<br />
K. A. Pyefinch (1955) e‘tablished the fact that the fundamental biological<br />
knowledge has hardly increased since the earliest times. He cites H. Boece<br />
(1527) and P. Olauen (1545 . -1614), who already knew the life history of<br />
the salmon in its main features.<br />
A. Fritsch arrives at a similar result in regard to the works<br />
of J. Johnstoni (1633) and Balbin (1679), who deacribed the life history<br />
of the salmon of the Elbe and mentioned the period spent in the ocean. C.<br />
Gessner (1958) Published.among other_things eready .'illustrations of the<br />
male and female salmon (Fig. 1). It. is thus the moresurPrising that Hckel
-5-.<br />
and Kerr very much later mention the.old male as a separate species (Salmo<br />
hamatus Cuv.). The conception of the oceanic life of the salmon that was<br />
developed . by.L. Roule (1929) at a time when a number of investigations of<br />
its food had already been published, is downright grotesqùe. According to<br />
a<br />
Fig. 1 a. Salmon male - Fig. 1 b. Salmon female (after Gessner 1558).<br />
a translation by H. Henking (1929) Roule. writes: "...stretched out to rest<br />
below the branches of the thicket of the white coral, below the fields of<br />
sponges and Pentacrinus, like the cattle below the trees of the forest<br />
and on the meadows, they fatten themselves on the prey that surrounds them...<br />
the darkness that envelops them would hardly bother iOthem, because their<br />
[p- 226]<br />
eyes are useless for the pursuit of their prey. They are surrounded by it -<br />
on all sides...they only need to seize their easy prey all around...They<br />
live there like cattle among their fattening fodder...."<br />
Several questions have occupied the researcher of fo rmer times
that are still problems for us. Thus already in the nineteenth century the<br />
threat of overtishing different waters had been pointed out. This call has<br />
been constantly repeated until today. It must, however, be mentiohed that<br />
such warnings were fOrmerly based more on intuition than on exact knowledge.<br />
Very much up to date appears the demand for tagging experiments<br />
by A. Fritsch (1893) and apparently little has changed until today, when<br />
one reads his remark that such expensive experiments were probably possible<br />
only in America.<br />
A review cif the problems posed in the literature on salmon shows<br />
that the statement by K. A. Pyef inch that the fundamental knowledge of the<br />
biology of the salmon has increased only little up .to the present day, can<br />
only mean that, although the older researchers actually did describe the<br />
life cycle of the salmon in its main outlines, it required later a great .<br />
deal of effort to provide exact proof for these statements. Even if Gessner<br />
considered already in 1558 the parr to be the young stage of the salmon, it<br />
remained for J. Shaw (1836, 1838) to provide the scientific proof for this<br />
assumption through a laboratory experiment. Furthermore, it must not be<br />
forgotten that only a few -sta.'t4en-s of the so-called life.cycle had been<br />
described, such as the ascent of the salmon into the rivers and the spawning.<br />
Today the river stage is well known in its sequence and one works now on<br />
partial problems in order to understand the governing mechanisms for certain<br />
effects. The majority of the publications until long after the turn of the<br />
century had a purely descriptive character. Today, however, very special<br />
questions are being studied that are supposed to contribute to the explan-<br />
ation of the causality of the phenomena. This is the one difference that<br />
distinguishes present day investigations from the older'ones.<br />
A further change consiste in that besidea the individuarbeing
treated as a quality, a special population i being treated as a quantity.<br />
This development has been pushed ahead by strong economic interests. The<br />
two spheres of problems can no longer be separated in the present-day stage<br />
of salmon research. When we attemPt to comprehend the'emigration of the<br />
young salmon into the sea quantitatively, then we establish chronological<br />
changes. The causes for such changes cari, however, only be discovered, when<br />
it is known which hormones effect a change that causes every fish to emig<br />
rate and, among other things, makes it resistant to . the higher salt concen-<br />
tration in the sea.<br />
The present paper is intended to treat problems of the biology<br />
and the study of the stock of the salmon in the Baltic Sea. In the sense<br />
sketched above the biology stands.here for the quality and the stock for<br />
the quantity. The goal of the investigations is to use the results reported<br />
on for a quantitative understanding of the stock of salmon in the Baltic<br />
Sea.<br />
For this end it is necessaxy to treat first the fishing technique '<br />
and the extent of the fishery. This chapter is intended to provide three<br />
important results for later discussions. The first task is to obtain a<br />
measure for, the intensity of the fishery and its changes. This is to make<br />
it possible to ascertain the effects of the fishing on the stock. The second .<br />
task is to ascertain yearly differences in the density of the stock. This<br />
enables us to recognize natural effects on the population density. Finally,<br />
we shall attempt to assemble the yields of the fishery that can be considered<br />
as a product of the intensity of the fishing and of the - amount of stock.<br />
. [P. 221]-,<br />
Measures for the intensity of fishing and the ameunt of stock.<br />
(ject, r)<br />
can only be obtained when the equipment uàed and its manner of action are<br />
known, and when furthermore the effects of external causes on the performarme.
- 8-<br />
(gea.r)<br />
of the eeipment can be discovered. These questions have therefore to be<br />
treated in detail.<br />
It should not be assumed a priori that the salmon are distributed<br />
uniformly in the Baltic Sea. It will therefore be attempted to enlarge our<br />
knowledge of the migration of the Baltic salmon and to find out whether<br />
the migration can cause distortion of oux measure for the amount of stock.<br />
Recruitment and spawning migration cause periodic changes in the<br />
stock. These have to be taken into account during the later analysis of<br />
the stock. As a means of judging the effects of the spawning migration we<br />
shall use the maturation of the oocytes. It will be attempted to use the<br />
various degrees of the development of the oocytes for an estimation of the<br />
proportion of the spawning migrants. In this connection other quantities<br />
can also be used comparatively. Such aids are the determination of the age<br />
and of the condition of the salmon. The latter is dependentpriiicipally on<br />
the food sUpply. For this reason we shall discuss also the results of in-<br />
vestigations into the kind and amount of food.<br />
Finally, the age investigations are required for other reasons.<br />
They provide in the first place the basis for a knowledge of the growth .<br />
conditions, the chànges of which permit conclusions regarding the effects<br />
of ecological factors. Furthermore, we require them for the determination<br />
of the losses from the stock.<br />
After the entire material required has been assembled, one can<br />
try to estimate the size of the stock and establish the magnitude of the<br />
losses that are caused during the sojourn . in the sea through natural causes,<br />
through fishing : and through - the spawning migration.<br />
. It can be stated already here that the present material has<br />
been obtained from the German share only in the entire - fishery (about 15
•<br />
-9--<br />
per cent). Furthermore, there are complicated external effects on the<br />
figures for the amount of the stock that cannot be eliminated entirely.<br />
Therefore, the first result of the stock estimations is not satisfactory.<br />
However, we are to find two criteria on hand of which it will be possible<br />
to establish the value of the investigations and that allow to make a second,<br />
probably better, estimate.<br />
In recent years R. endler (1958-1964) has made salmon inves-<br />
tigations in Germany. He has worked principally on a special statistics<br />
of the number of fishing cruises and. of the landings at the Kiel sea-fish<br />
market in regard to their composition according to weight categories and<br />
concerning their amounts in different years. An earlier paper (R. Kândler<br />
and M. Whmann 1957) concerned age determinations during the three catch<br />
periods 1952/5 to 1954/5. However, the length7groups were not taken into<br />
account according to their relative frequency in the catches in these in-<br />
vestigations. Such quantitative data were required for the present work.<br />
During the six fishing periods 1957/8 to 1962/3 I have supplied<br />
86 cutter captains with diaries for daily entries of catch results and con-<br />
ditioneof the environment. In this way entries for more than 7000 fishing<br />
days could be worked out. These communications were supplemented through<br />
the participation of scientists in 13 fishing cruises with a total of<br />
.almost 200 days at sea. On these cruises we could also preserve the ovaries<br />
of 70 salmon females. Food investigations were carried out at sea and in<br />
the laboratory on 2400 salmon. From January 1958 until April 1963 samples<br />
of scales for age determination were collected from about 7000 salmon. -<br />
During the same period it was possible to measure and weigh more than<br />
16,000 fish. •<br />
These extensive investigations were supported through finâkial<br />
•
•<br />
•<br />
- 10 -<br />
contributions from the Deutsche Wissenschaftliche Kommission fer Meeres-<br />
[P. 228]<br />
forschung (German Scientific Commission for Oceanography [GSC0]). For<br />
special investigations, the testing of new drift nets, and the selective<br />
tests with fish hooks, the Federal Ministry for Nutrition, Agriculture,<br />
and Forests made funds available.<br />
Prof. R. Kandler, who directs the German salmon research, has<br />
supported the present investigations not only in regard to organization,<br />
but has also stimulated it scientifically and given directions. I should<br />
like to thank him for numerous clarifying discussions and conversations.<br />
Important help has been given by Dr. G. Ohlmorgen-Hple through<br />
taking.part in 5 of the 13 cruises. The work done on board under very prim-<br />
itive conditions and in winter, deserves high praise.<br />
In the market analyses of the Kiel seafish market and in the<br />
evaluation of the material.I had the help of the technical assistants Miss<br />
U. Behrens and Miss H. v. Kistowski and also of Drs. F. Lamp and G. Rauk.<br />
I am very grateful to the manager of the Fischverwertung Kieler Ferde, Mx.<br />
Koschies, who showed great understanding and gave the permission for the<br />
market research.<br />
My appreciation and special thanks axe extended to the many<br />
cutter captains and salmon fishermen, who provided space on board, kept<br />
. the diaries, collected salmon stomachs ancthelped with the market inves-<br />
tigations.<br />
2. The salmon fishery<br />
in the Balt , ic Sea<br />
2.1. The historical development<br />
B. Benecke (1881), who has carefully studied the documents on<br />
the Teutonic Order in East- and West-Frussia, as fax as they concern the<br />
•
•<br />
- 11 -<br />
fishery, mentions the granting and sale of fishing rights in the inland<br />
waters by the Order for the first time in the 13th century. It is also<br />
stated that at the end of the 14th century vessels sailed from Danzig to<br />
Schonen and Bornholm for the herring fishery. There is, however, no mention<br />
of salmon fishery in the Baltic Sea.<br />
On March 30, 1302 the preaching monks of Elbing received the<br />
right to fish in the Frische Haff and in the ocean with one "keitel"<br />
(trawl-fishing) each. Pkeitel" = an unwieldy Baltic Sea fishing boat,<br />
? still in use today, trs1.1. This is the first reference to coast fishery.<br />
• However, it appears not to have played any role in comparison with the<br />
inland fishery.<br />
•<br />
In 1409 the grand maéter of the Teutonic Order sent salmon to<br />
the king of Hungary and to King Wenceslav of Bohemia in order to obtain<br />
their help in a quarrel. In 1440 the salmon brings at least the tenfold<br />
price of the pike. In 1621 it is prescribed that the salmon is not to be<br />
given to merchants, but must be surrendered to the feudal fishmaster,<br />
because it belongs exclusively to the feudal master. In 1641 . 220 salmon<br />
had to be delivered through the fishmaster to the town of Elbing for the<br />
supply of the notabllities. At that time the salmon does not eepear to<br />
have been a fish in mass supply in East- and West-Prussia. The legend that<br />
servants stipulated in their contraot not to receive salmon as food more<br />
than once a week, which is current in the most divers fishing areas of the<br />
world, certainly does not hold true here. This fish has rather stood in<br />
high esteem until today and has alw«ys commanded a high price and has been<br />
a food fish for kings, rather than for servants. •<br />
Until the end of the 16th century only the fishery in inland<br />
Waters is mentioned in the statutes. However, in 1751 N. C. Gisler reports..
•<br />
•<br />
- 12 -<br />
that the salmon migrate from the rivers in northern Sweden into the<br />
southern Baltic Sea. He derives this knowledge from the fact that al-<br />
[p. 229]<br />
ready in 1728 salmon caught in rivers -in northern Sweden were feund to<br />
contain fishhooks of iron and braàs that were used, according to the Royal<br />
Academy of Science, principally as cod hooks in Gotland, bland and in<br />
Blekinge, but not in the Gulf of Bothnia.<br />
The migration is, however, of no interest for us at the moment.<br />
The remark of Gisler is actually the oldest reference to the practice of<br />
hook-and-line fishing for salmon in the Baltic Sea. In the older works of<br />
and Balbin (1679) (after A. Fritsch 1893) is mentioned<br />
I. Johnston (1633)<br />
only the rise of the salmon into the river Elbe for spawning..<br />
B. Benecke (1881) lists the following contemgrary equipment for<br />
the river salmon fishery: seines and salmon traps (spring traps) and for<br />
the coast and bay fishery he mentions beach seines, set nets, as well as<br />
salmon baskets. He writes furthermore that the salmon set lines had beer.<br />
introduced by Pomeranian fishermen into East Prussia where they proved<br />
very successful.<br />
Since there hgd previously been no lino fishing along the coast<br />
in East- and West-Prussia, it is possible that the salmon described by<br />
Gisler concerned fish that hadcome from the Pomeranian coast.<br />
The salmon fisherman Karl Madsen from egenwalderende, who<br />
was born in 1881, provides information about a pelagic catch of salmon<br />
at a distance of 10 to 15 nautical miles from shore. He had learned earlier<br />
from older relatives that anually in Nàvember a fleet of sail Mats, 7 to<br />
8 m long, sailed from Farther Pomerania more than 250 nautical miles to .<br />
Liepnja ("Liebau"), in order to fish there for salmon with set lines,<br />
200 to each boat, until Christmas. The fishermen lived during this time.<br />
•
•<br />
- 13 -<br />
in LiepUva. These voyages ceased about the year 1875, because the small<br />
vessels had sunl_s in a storm. After this the'Pomeranians fished together<br />
with the Danish fishermen annually from October to March near Hela. Not<br />
much later Swedish salmon fishermen crossed the Baltic Sea in their sail<br />
boats from Schonen in order to catch salmon with driftnets along the coast<br />
of Farther Pomerania and in the Danzig Deep.<br />
ItES<br />
After the foundation of the(International Board for Oceanogrphy<br />
salmon research grew enormously. Since about 1900 many countries liberate<br />
salmon fry that have been obtained through artificial fertilization of thé<br />
eggs, as well as young and have carried out tagging experimenis , (Sweden<br />
since 16°). The publications that have been stimulated by the Board now<br />
give also the first indications of the fishing in the Baltic Sea. From<br />
Denmark (Bornholm) and Finland (Gulf of Bothnia) we have reports on the<br />
of salmon since 1886. Soon there appear also descriptions of the<br />
landings<br />
manner in which the salmon fishery was being carried out (Trybom and Wolle-<br />
back 1904, Petersen and Otterstr8m 1904, Henking and Fischer 1905, Sandmann<br />
1906, Trybom 1910, Henking 1913, 1916 and 1931, Nordquist 1924).<br />
In the northern Gulf of Bothnia fishing is done mainly in the<br />
vicinity of river moùths with setnets during spring and fall. These nets<br />
are not anchored but are suspended from posts. In part,•several nets are .<br />
arranged so that they work like a basket. In the Gulf of Bothnia are used<br />
dragnets (120 x 5 m, 60 mm mesh). One also uses herring baskets for the<br />
capture of salmon. In-Finland, where the salmon stands in second place<br />
behind the herring in importance, one.fishes in winter with salmon nets<br />
under the . ice. •<br />
In the central Baltic Sea, on the southern coast,as well as<br />
on the northern Coast, set lines played the greatest role_from fall. iill
- 14-<br />
winter; and driftnets during 'spring. The line fishery is carried out about<br />
20 nautical miles from shore, whereby each cutter works with 40 to 60 hooks<br />
(Schonen) or 60 to 90 hooks (Bornholm), in later years with up to 200. In<br />
Sweden and Denmark each setline•is- equipped With three to five hooks, in<br />
Germany and Poland each has ene hook. The fishing with.driftnets takes place<br />
close inshore. These nets are about 35 m long, four to eight m deep and<br />
they have mesh widths of 60 to 90 mm (from knot to knot). Each cutter fished.<br />
[P. 230]<br />
with 30 to 50 hempen nets. At Bornholm and at the coast of Pomerania one<br />
used in summer.and fall on the beach also setnets and dragnets (seines).<br />
• • About the year 1908, which brought in many districts the motor-<br />
ization of the sail boat, there occurred a temporary change in the structure<br />
of the Swedish fishery at Schonen. The driftnet fishery that had hitherto<br />
• been so important, was . replaced by the fishing with setnets. Only 11 sail<br />
boats still sailed from Schonen with driftnets or crossed the Baltic Sea.<br />
The importance of the line fishery declined sharply.<br />
In the subsequent years, between the two World Wars, setline<br />
' and driftnet fishery have consolidated their primary position, although<br />
beach seines were still used for fishing (K. Bahr 1936).<br />
The Swedish driftnet fishery experienced an enorMous advance<br />
about the end of the Second World War and the subsequent years. At about<br />
the same time Danish fishermen from Hundestedt developed the-entirely •<br />
novel driftlinè fishery. This concerns a pelagic longline, which ié composed<br />
of several hook sets.<br />
To begin with, 400 to 500 hook Sets and very'long-shanked hooks<br />
with about 20 mm - span were.being used, the number of hook sets that were-<br />
carried by each cutter, however,.increased steadily during:the next'20 -•<br />
yearS (Table 1).
•<br />
1948/49 545<br />
1949/50 730<br />
1950/51 770<br />
1951/52 920<br />
1952/53 800<br />
1953/54 950<br />
1954/55 1000<br />
1955/56 1200<br />
1956/57 1220<br />
1957/58 1370<br />
1958/59 1500<br />
1959/60 1580<br />
1960/61 1700<br />
1961/62 4743<br />
1962/63 1722<br />
60<br />
80<br />
90<br />
100<br />
100<br />
110 827<br />
110 870<br />
110 1042<br />
120 1055<br />
191 1182<br />
220 1289<br />
237 ' 1264<br />
287 1435<br />
306 1249<br />
.316 1449<br />
12<br />
4<br />
3<br />
• 14<br />
2<br />
6<br />
2<br />
3<br />
7<br />
155 29<br />
191 9<br />
197 • 11<br />
225 9<br />
246 9<br />
281 9<br />
- 15 -<br />
At the time of writing, driftnets and driftlines are of- surpas-<br />
sing importance for the pelagic salmon fishery in the Baltic Sea. It can,<br />
however, be stated that the extent of net fishery has increased . steadily<br />
ana it is at present of greater importance in the Federal Republic than<br />
the driftline fishery.<br />
By way of summary one can distinguish historically three dev-<br />
elopmental periods in the salmon fishery:<br />
(a) pure river fishing, to about the beginning of the 18th centurY,<br />
(b) predominantly river fishing, alongside of it the increasing importance<br />
)<br />
of shore fishing until about 1945,<br />
predominantly pelagic fishing with driftlines and driftnets, in addition<br />
river and shore fishing: •<br />
Table 1. Number of drifthooks and driftnets per vessel that<br />
were carried by German boats in salmon fishing<br />
(according to questioning of and to questioreires sent to salmon fishermen)<br />
Average number Average daily Number of<br />
.Season. of setting of . cutters<br />
hooks nets hooks nets concerned<br />
2.2. The technique of catching<br />
The kind of vessel and gear employed at any•moment-dePende on<br />
whether the fishing is carried out in the rivers, along shore or in the .<br />
open Baltic . Sea. ' •<br />
[P. 231]
•<br />
- 16 a -<br />
Fig. 2. Catching salmon with the "not" in the Indalelven<br />
(alter Svârdson 1957).
• 2.2.1.<br />
River fishing<br />
- 16-<br />
The most important fishing equipment for catching salmon in the<br />
northern rivers of the Gulf of Bothnia is the "karsinapator". In ground<br />
plan the device is constructed like the chamber of a basket. The four-<br />
cornered chamber is formed of posts driven into the river bottom, which<br />
stand at such a distance that the salmon can swim through between them.<br />
Forthe catch one spreads a net on the upètream side of the chamber; after<br />
this a second net is drawn through the chamber from the opposite side as<br />
far as the first net. The salmon caught between the two nets can afterwards<br />
be taken on board together with the gear. -<br />
In almost all rivers of the Gulf of Bothnia and in the rivers<br />
of southern Sweden the fishery is carried out in addition with the "not".<br />
This is a beach seine of varying size (see Fig. 2). Besides these two Im-<br />
portant devices . there are also in use fishtrapè that work on the principle<br />
that a side arm of the river can be laid almost dry. In addition simple<br />
• weirs serve to catch the ascending salmon.<br />
besides seines.<br />
2.2.2. Shore fishei.y<br />
In the Soviet rivers of Latvia gill nets are also being used<br />
The most important equipment for the shore fishery in the Gulf<br />
of Bothniaris the trap net (etommer) in which are also caught herring.<br />
Alomg the shores of Ingerman Land winter fishing is carried oUt with draw,.<br />
nets underneath the ice. Of considerable importance are also the Finnish _<br />
set mets that are frequently set in the form of a basket. Driftnets and<br />
set lines occur also in Schonen and Blekinge; there, as well-as in Gotland<br />
the seine also plays a certain role.'<br />
In the Gulf of Riga the herringimskets are also.the most '.<br />
[P. 232]
•<br />
•e<br />
717-<br />
important catching device for salmon, beach seines and driftnets are being<br />
used in all remaining coastal regions.<br />
The vessels used in coastal fishing are mostly.open.boats.<br />
2.2.3. Pelagic salmon fishing'<br />
Danish, Swedish, German, and Polish fishermen are exploit4ig<br />
the stocks of salmon in the central Baltic Sea with drift-longlines and<br />
driftnets. •<br />
. 2.2.3.1. Vessels<br />
The salmon cutters have a length of 12 to 14 m and are equipped<br />
• with engines of .f rom 50 to 350 HP. Two-way radio and echo sounders bèlong<br />
to the standard equipment. Widely used are also radio direction finders.<br />
Decca and radio position finders, electrical and hydraulic steering equip- .<br />
ment have already been installed in some boats.<br />
The fuel tanks hold from 3000 to 6000 1 diesel fuel. This cor-<br />
responds to a cruising range of from t000 to 42000 nautical miles. A few<br />
vessels have refrigerated fish holds, where the temperature is held near<br />
freezing point, with a correspondingly gmaller consumption of ice. For One<br />
voyage about 3 t of ice are required. The crew consists of the captain and<br />
three men (mechanic, boatman, and cook). The accomodation for the captain<br />
• is in the wheelhouse and the other crew members are housed in the bow. .<br />
2.2.3.2. Fishing equipment<br />
As has already been mentioned, hooks and gill nets are carried<br />
as fishing gear. Salmon driftnets Consist> of a floating rope With floats,<br />
norsels, leaders and net They are single-Walled gill nets, which in Ger...<br />
, many are today made from nylon (formerly hemp 6/3). The net .(nylon 210/12,<br />
border mesh 210/15) is about 309 meshes long and 40 to 60 _meshes deep. •<br />
Until - recently the leader was madeof nylon 210/24, since introduction of .<br />
ring nets (Fig. 3) a.foot rope of 1 to 2 mm diameter is, being.used. There
- 18-<br />
are 50 norsels, 60 to 80 cm long, which are laid double from nylon 210/27<br />
or from spun nylon 20/12. The net is adjusted at the leader at 1/3 and<br />
.the leader is adjusted at the floating rope at 5/6 (6 meshes on 5). The<br />
line (formerly hard-laid sisal, 7 mm diameter) consists now of laid mono-<br />
fil propylen of 5 mm diameter. Six conical or cylindrical floats of plastic<br />
(Plarex or foam plastic 13 x 8om) replace the formerly used cork floats.<br />
Driftnets were formerly used only during the spring months from - .<br />
March till May. The winter with strong windstorms was at first considered<br />
to.be entirely unsuitable for net'fishing. The hempen nets that were pre-<br />
• . ponderantly in use until 1960 and the "perlon nets" that were tried out •<br />
hesitantly could hardly be used in winds of over 4 on the'Beaufort . scale,<br />
In a stronger wind the pull on a laid line became so strong that it began<br />
[P. 233].<br />
to untwist and thus rolled Up the entire net. This event was much dreaded<br />
by the fishermen, because the straightening out of the net could take selp-<br />
eral days. They thus incurred not only the loss of catch during the stormY<br />
night, but also on the following days.<br />
Many fisherMen were also afraid to set out hempen nets when it<br />
became necessary to stow them wet on deck on account of unfavourable weather<br />
after they had been used only once or twice. Rotting then proceeded very<br />
P. 234]'<br />
quickly, depending on the temperature. - There remained thUs at first only "H<br />
the possibility to extend the drift fishery into the fall months and to<br />
begin the catch already in August and September, when line fishing does<br />
in general nôt yet give l any results. •<br />
The further development, the carrying out of the net fishing.<br />
during thirwinter months from November until February:, was prevented Eie<br />
long as hempen nets remained in use. However, the nets made of synthetic<br />
fibres found at first no aOceptance. - During the first trials it had'been
FA<br />
(6) .<br />
• .4><br />
•• se<br />
- 19 -<br />
found that the net floated on the surface of the water on account of its<br />
light weiet and the lack of absorptivity and later it aléo became tangled<br />
in a light seaway. Through the addition of a sinker line at the bottom.the.<br />
gear lost some of its catching ability.<br />
Fig. 3a. Salmon driftnets with rings at the norsels.<br />
A - attachment of the end norsels, B - foot rope, F - float, H - norsel,<br />
R - nylon ring, S - leader ), W - swivel. ,<br />
_ . .<br />
• .<br />
Fig. 3b. Salmon driftnet with simplellorselsi lettering as In Fig. 31<br />
.<br />
Unfortunately, I have . only few comparative figures for the cat-<br />
ching performance of hempen and Synthetic nets. The results show 'rather •<br />
better catches for perlon nets, but the - differences are,not statistically<br />
significant on account of the scant material. The probàbil#Yr, tbet.pèrleli
•<br />
nets give better results is only about 55 per cent (Table 2).<br />
Table 2. Catching performance . of synthetic and hempen nets.<br />
Date<br />
Number of Number of salmon<br />
sets per 100 nets<br />
hemp perlon hemp perlon<br />
Spring 195 8 380 5 345 11.31 11.59<br />
Spring 1959 2874 474 4.66 5.90<br />
Fall 1959 21 6 54 2.77 9.25<br />
Szatybelko (1957) has examined the catching potential of salmon<br />
gill nets. In his experiments he compared, among other things, the perfor-<br />
mance of 45 fine-yarn nets (cotton) with 45 coarse-yarri nets (hemp). The<br />
cotton nets were in part setnets and in part driftnets, both with selvedges<br />
and a foot rope at the bottom. The mesh was 65 mm, the yarn number 135/6.<br />
Ike hempen nets, in contrast, were made up as driftnets without a foot<br />
rope and sinker line and they had a mesh of 85 to 90 mm and yarn numbers<br />
of 4.8/3 and 6/3. The catching results were 0.33 salmonids per cotton net<br />
and day compared With 0.93 per hempen net and day. The total effort las<br />
not been given. Notwithstanding the different mesh, the average weight of<br />
the fish was 4 kg for both nets.<br />
If we flow come back to the goal to extend the driftnet fishing<br />
into the winter months, we can only state that it was not possible to at-<br />
tain this with hemp nets and nylon nets of usual manufacture . For this<br />
reason nylon nets of a different design were employed for the first tiee<br />
during the spring of 1959 (Thuow 1959).<br />
In this design the net sheet is independent of the rotation of<br />
the . line, because the norsels are fastened to rings that'Can move on the<br />
line. Five cylindrical or conical plastic floats have been threaded on the
•<br />
line.<br />
- 21 -<br />
. In order to obtain further protection against rolling up of the<br />
net, the end norsels of each aheet can be fastened to a brass swivel in-<br />
stead of directly to the line (Fig. 3).<br />
The ring nets showed their superiority over the traditional geaX<br />
already during the very first tests. Now fishing was caxried out in winds •<br />
of up to 6 on the Beaufort scale (formerly 4). A comparison with hemp nets<br />
is, however, no longer possible, because most of the cutters are now equipped '<br />
exclusively with synthetic nets. At present ten cutters are employing' ring<br />
nets. In 1960 two Danish fishermen also switched to this design. Other cutters<br />
adopted foot ropes and floats for the nylon nets of traditional design and<br />
obtained through this also a certain improvement. Since 1960 monofil nets<br />
[P. 235] .<br />
have been tested to a small Sxtent. Because the material is too stiff such<br />
gear is hardly being used today. Recently (1963/4) synthetic nets made in<br />
Japan have been used, made of yarn into which a heavier fibre is supposed<br />
to have been spun.<br />
Driftnets are set so early in the afternoon that the fleet is<br />
on the water by sundown. Formerly they were picked up around sunrise. Sincé.the<br />
number of nets exceSds 400, however, the taking7 up . begins around midnight.<br />
A drift-longline (Fig. 5) is composed of a line of cotton 20/36<br />
to 50/75, 8 to 10 fathoms long, more rarely: of braided nylon staple-fibre<br />
(average 1.6 mm), with an attached float and the leader with hook..The leader<br />
consists of perlon wire (o.6 mm) and. is 3.0 to 4:5 fathoms long. It is fas-<br />
tened to a small brass swivel, which is threaded on the line and.can slide<br />
on it between two knots about 25 cm apart."The hooks are at present mainly<br />
typé Mustad No. 2/0 (13.5 mm between peint and shank) and to a gmaller ex-<br />
:tent Mustad.No. 3/0 (15 mm between point and shank). The lead sinker•(- ea g)<br />
is attached about 1 m above the hook. When the hooks are being assembled,
•<br />
•<br />
G<br />
Fig. 4. End buoy for salmon fishery with<br />
driftlines and driftnets.<br />
G = incandescent bulb.<br />
F - flag<br />
N wet battery<br />
B iron mounting<br />
S float<br />
L<br />
Fig. 5. (above) salmon driftline—(below left) attachment of.<br />
the leader on the line - b (below centre) attachment of the<br />
hook to the leader - c (below right) float.<br />
B - sinker-, K-- knot, L --line, S.- float,<br />
. V - leader, W - swivel.<br />
- 21 a -
-•22-<br />
the free end of the line is knotted to the loop of the float of the fol-<br />
lowing hook so that a continuous line results (the "lank") 1 . It can com-<br />
prise'2000 hooks and is then about 35 km long. In the water the gear ex-<br />
tends over a distance of about 15 nautical miles (27 km).<br />
..ScowÀlerelo.AC)<br />
The bait consiste of sprat or pieces of trigger fish about 1.5<br />
[ P. 236],<br />
cm wide. In the fall the fishermen prefer trigger fish, which should be<br />
as small as possible, in the winter they prefer sprat.. However, both<br />
species may be used simultaneously.<br />
The setting out of the driftlines begins between 0200 and 0400<br />
hr, so that the last hook is in the water before dawn. Between 09O0 and<br />
1000 hr the taking up of the gear begins.<br />
. .<br />
In the near future Danish, Swedish, and German fishermen will<br />
. be allowed to use 'only hooks of 'the type Mustad No. 6/0 of a new kind .<br />
Table 3. Distribution of the' On account of a Swedish request<br />
length of sprat used as bait.<br />
an agreement has been reached bY the three<br />
Length (cm) Width (cm) Number countries, which . permits the fishermen to •<br />
1 0 .5<br />
11.5<br />
12.5<br />
13.5<br />
14.5<br />
2.2<br />
2.4<br />
2.6<br />
2.6<br />
3.0<br />
1<br />
' 25<br />
13<br />
4<br />
1<br />
.<br />
'<br />
use only hooks with the larger span (19 mm<br />
between point and shank). This agreement '<br />
raised the question of selectivity of hooks<br />
of different sizes. If we start from the<br />
consideration that the selectivity is determined by the relation between<br />
the size of hook and bait on the one hand and the maximum mouth opening'<br />
of the fish on the other.hand,:then we can establish the following: the<br />
sprat used as bait are 11 to 14:cm long, they have an average length of<br />
12 cm and a width of 2.5 cm.' A salmOn that has been caught on a hOok baited<br />
1 from the Dani .sh "laengde" ='length.
• with<br />
•<br />
Total length<br />
(cm)<br />
Mouth opening<br />
percentage of<br />
mm length<br />
- 23-<br />
sprat has thus a mouth opening of at least 2.5 cm between the jaws<br />
(Tables 3, 4).<br />
Table 4. Mouth opening in salmon<br />
and sea trout between jaws.<br />
According to Table 4 this ap-<br />
plies only to salmon of over ca. 27 cm<br />
total length. We have to reckon, however,<br />
with the fact that only a part of the<br />
. fish of this length take this bait, be-<br />
15.1 1 15 9.9<br />
16,5 1 17 10.3 • cause the selectivity is spread over a<br />
17.1 1 16 9.4<br />
24. 6 24 9.8 • certain range of lengths.<br />
34.4 35 10.2<br />
39 29 7.5 In the above statements we -<br />
50 49 9.8<br />
56 48 8.6 started from the fact that the selectiv-<br />
56 • 55 9.8<br />
56 5 8 10.4 ity is determined substantially by the<br />
6o 55 9.2<br />
61 59 9.7 size of the bait, as long as the shank<br />
62 63 10.1<br />
distance of the hook is less than the<br />
1 Sea trout<br />
width of the sprat. This means at the<br />
same time that the different sizes of hooks probably have hardly any<br />
influence on the selectivity. It will be, however, quite certain that such<br />
an influence will be hidden by accidental changes in the catch, when the<br />
spread of the hooks tested should be small.<br />
The questions mentioned above could .be investigated in more<br />
detail in 1959 to-1962. During that time.ten fishing cruises were under-<br />
taken in order to clear up the selective effect of the different sizes of<br />
hooks.<br />
In the trial hooks of 10.5 and 15.0'mm Opening were tested<br />
against those of 19 mm opening. Thtis the difference was 4.0 to , 5.5 mm,<br />
that is, about 20 to 30 per cent. The results showed that salmon over 30<br />
cm length took .both kinds of hooks. These fish have an average mouth opening:
- 24-<br />
of almost 29 mm. More than 93 per cent of all fish caught were, however,<br />
more than 60 cm long. Such salmon have a mouth opening of more than 57 mm.<br />
This Means that a mechanically conditioned selection does not take place<br />
in this range of lengths. If there is still some kind of selectivity at<br />
work, it must be conditioned by sensory physiology.<br />
LA. 237]<br />
In contrast to this expectation the trial results showed relat-<br />
ively small differences between the catch results for both kinds of hooks<br />
for lengths of up to 74 cm. For lengths of over 60 cm more salmon were caught<br />
with the large hooks than with the small ones.<br />
Tests for significance for the catch differences between the<br />
two kinds of hooks for the total catch, as well as for fish above 89-cm .<br />
length showed no statistically significant differences. It thus remains<br />
whether<br />
to establish in case a selective effect has been presentlit has been cov-<br />
ered up in the present case by accidental fluctuations in the catch.<br />
2.3. The extent of the pelagic salmen fishery . .<br />
2.3.1. The fishing grounds<br />
It has already been mentioned that the salmon fishery has ex-.<br />
a large extent to the open Baltic Sea only alter the Second<br />
World War. To begih with the fishermen frequented only parts of the<br />
southern Baltic Sea. The most important fishing ground was the Bay of Danzig<br />
(south of 55 ° N). At that time the southern point of Gotland Deep (south .<br />
of 56 ° N) also played already a certain role, as well as the Bornholm Basin.<br />
In the spring months the coast of Pomerania was visited.<br />
During the course of the years it was principally the Danish<br />
fishermen who extended their cruiees to the more distant'fishing grounds.<br />
At the beginning of the fishing season, in August, todayeevere Danish .<br />
and a few German cutters sail past the Land. Islands and . visit:the Gulf<br />
tended to
•<br />
•<br />
- 25-<br />
of Bothnia. In the fall the fleet moves southwards to fish the region<br />
between Gotska Sand8 and bsel, as well as the eastern Gotland Basin. In<br />
the fall of some years good catches are made also near Visby and bland.<br />
During the main period for line fishing (December to February) the<br />
Danzig Deep, bounded by the cornerpoints Rixh8ft, Mittelbank, Memel, and<br />
Kahlberg still remains the most important fishing ground. During this time<br />
fishing also takes place neax Bornholm. With this the entire Baltic Sea<br />
between about 54 ° N and 63 ° N serves as fishing ground for the driftnet and<br />
driftline fishery. The Gulf of Finland and the region west of Bornholm<br />
have hitherto not been fished (Fig. 6).<br />
2.3.2. The fishing season<br />
For biological and climatological reasons two fishing.periods<br />
have to be distinguished during the course of the year: the summer, with<br />
small landings, and the colder season with good yields.<br />
Because windy and stormy weather predominates during the period<br />
of best harvests, hitherto only driftlines• have been used exclusively.'<br />
During spring and later also during fali, fishing with driftnets predomin-<br />
ated. The Danish fishermen prefer this division until the time'of writing,<br />
because the driftline fishery still plays an important role for them.<br />
Fishing from Gotland is carried out in a similar manner. In contrast,<br />
driftline fishing is of little importance for the Swedjàh cutters fro*<br />
Blekinge. There driftnets are the main gear. Until 1960 the fishing aeason<br />
for the German cutters was divided in a manner similar to that in Denmark.<br />
After the introduction of synthetic nets one switched, however, more and<br />
more to driftnet fishing also during the winter.months. Since then, salmon<br />
fishery is being carried out from August to June predominantly with dxift-<br />
'nets, line fishing, however, is being used only during the winter mdenths,
•<br />
when stormy weather prevails.<br />
66<br />
65<br />
64<br />
63<br />
62<br />
61<br />
60<br />
59<br />
58<br />
57<br />
56<br />
55<br />
54<br />
15. . , . 20 25<br />
Fig. 6. The salmon fishing grounds in the Baltic Sea.<br />
2.3.3. The yield of the stock,<br />
- 26 -<br />
In Table 1 it has been shown that the salmon fishing industries<br />
lave during the last . 15 years augmented considerably their efforts to<br />
Lp.238]<br />
[P. 239]
•<br />
•<br />
- 27-<br />
increase the catch. Such endeavours always raise sooner or later the ques-<br />
tion about the degree of exploitation. One attempts to learn up to which<br />
*k>c.K •<br />
• limits a crop can be.stressèd, how many fish can be taken without a con-<br />
sequent impairment of future yields. For this it is necessary, to begin<br />
with, to find yardsticks for the exploitation. In this connection we shall<br />
here discuss the fishing effort and the population density.<br />
2.3.3.1. Fishing effort<br />
As fishing effort will be considered in the wide sense all<br />
outlays for the purpose of catching fish. The number of vessels, of the<br />
sailings for fishing, of the fishing days at sea and of the fishing gear<br />
can express the fishing effort. A demand that has to be met by the fishing<br />
effort is its direct relation to the exploitation of the stock, whichshall<br />
be considered to be initially represented by the yield. We consider there-<br />
fore that the best criterion for the fishing effort is the number of the<br />
fishing gear set out during .a fishing season. For the determination of<br />
these values it will be necessary to know also the number of fishing days.<br />
Table 5. German fishing effort<br />
in the Baltic Sea ProPer.<br />
Number of gear x 10 6<br />
Season Total effort<br />
Nets Hooks expressed<br />
as hooks,<br />
1954/6 _ - 3.21<br />
1955/,6 - 2.32<br />
1956/7 0.079 4.62 4.91<br />
1957/8 0 .108 3.57 4.44<br />
1958/9 0.180 2.47 3.49<br />
1959/60 0.200 3.00 4.38<br />
1960/1 0.350 2.27 4.74<br />
1961/2 0.400 3.32 5.57<br />
1962/3 0.303 1.70 3.62<br />
I was able to obtain such<br />
values for about one-third of the total<br />
German landings through excerpts from<br />
logbooks and through the issue of<br />
diaries to 10 to 20 fisherken for<br />
daily entries. These are used is the<br />
basis for the calculations for the<br />
total German effort.<br />
In Table 5 are shown the<br />
values for the catches of driftnets<br />
and driftlines. The two figures can',
•<br />
.<br />
- 28-<br />
however, not be compared directly with each other, so that the trend of<br />
the development of the effort is not .easily seen. Therefore, the total lan-<br />
dings have been re-calculated as values for hooks with the aid of the diary<br />
entries.<br />
There is an increase in the total effort by more than one-third<br />
since the season of 1957/8. This deyelopment was interrupted by the col d .<br />
winter of 1963, because the German cutters could not fish from January<br />
until March 1963.<br />
It is our goal to obtain an expression for the exploitation of<br />
the stock of salmon. The extent of the exploitation is, however, dependent<br />
not only on the number of the gear employed, but also on the spatial dis- .<br />
of the effort and of the fish. That is, it will be necessary to tribution<br />
.<br />
take into account besides the spatial distribution of the effort, also the<br />
number of fish on the various fishing grounds. This value is the total ef-<br />
fective fishing intensity. It is, however, not possible in our case to ob-<br />
tain for this any values that are approximately correct, because it cannot<br />
be ascertained how the entire fleet was . distributed over the fishing grounds<br />
and what yields were obtained on the individual fishing grounds. This forces .<br />
us to consider the effort as the measure : for the exploitation of the stock.<br />
P. 240]<br />
2.3.3.2. Catch per unit effort<br />
In the above the yield of the fishery has been accepted as the<br />
expression for the exploitation of the stock in order to make more plain<br />
the role of the fishing effort. It can, however, easily be seèn that the<br />
intensity of fishing is proportionaLto the exploitation only when the size •<br />
of the stock remains constant. In contrast to this, a constant intensity<br />
of. fishing can lead to strong depletion when the stock is very weak, whereas<br />
it does diminish a strong stock only slightly. This shows that the intensity<br />
•
• of<br />
•<br />
fishing representsavalue for the measure of the exploitation that is<br />
necessary, but not sufficient. It has to be supplemented by statements<br />
about the strength of the stock or about the population density. The "eap=.<br />
cebk<br />
leue..e per unit effort" is customarily used as such a measure. It stands in<br />
close connection with the effort. If we put this in relation to the yield<br />
obtained, we shall have statements that are directly comparable with etich<br />
cate.k.<br />
other. We call the yield per unit of the gear employed the aretliee per<br />
unit effort. In the present case it will be given as the number of salmon<br />
per 1000 hooks or per 100 nets.<br />
This unit hés already been used for the determination of the<br />
effort and in the course of this work we shall have to come back to it<br />
frequently in order to explain phenomena or to make them clearer. For this<br />
are extraordinarily important. The fact alonè •<br />
ct,td,„<br />
. that the captuTe per unit effort is to be considered as a measure for the<br />
strength of the stock, demands a critical analysis when ascertaining these<br />
data. To begin with, it has therefore to be examined whether the results<br />
• of the catch are being influenced by factors that have their cause not in<br />
the stock. In.Other words: is the capture per unit effort a value that is<br />
composed of several factors of which the strength of the stock of salmon<br />
is only one? •<br />
Let us consider for a start the monthly changes in the oebliàe<br />
per unit effort. We must expect during the course of the season a steady<br />
reduction of the stock through fishing and other effects. As far as the<br />
catches<br />
strength of the. stock ié concerned, the ceptueas per unit effort should:•<br />
diminish steadily from fall to spring.<br />
However, the monthly. trend in Table 7 does not show such a<br />
.course. The values of the line.fishery rather rise until December, those<br />
. ,<br />
in the net fishery xise in part until February, only to fall until 'June<br />
•<br />
reason, these statements
Mittel zg Mean<br />
1956/57-1961/62<br />
Mittel<br />
1960/61-1961/62- • 9,7<br />
cted,e s<br />
Table 7. German ouptemee per unit effort.<br />
(eAgorrected)<br />
Weigh-<br />
Season Aug. Sept. Oct. Nov. Dec. Jan. Feb. . March Apr. May June ted Simple XI - III<br />
mean mean - •<br />
Salmon per 1000 hooks<br />
1954/55 (20,2) (14,6) (13,5) [ 7,9] (13,2) 14,0 13,9<br />
1955156 • '<br />
( 8,3) ( 8,7) 6,0 - 21,6 9,1 11,4 11,2<br />
1956/57 1 12,3 - - 19,4 26,7 25,2 10,3 24,1 (9,3) 18,9 21,1<br />
• 1957/58 10,8 10,5 15,9 12,0 6,3 3,1 [4,7] 11,6 9,6<br />
• 1958159 . ( 4,6) 15,7 32,4 17,2 17,9 (12,2) (6,0) 18,1 19,1<br />
1959/60 12,9 8,7 9,3 7,5 7,2 ( 7,3) •<br />
• 8,8 8,0<br />
1960/61 - 10,0 11,9 11,5 14,1 9,8 ( 5,1) [0,4] 11,6 10,5<br />
• 1961/62 . , 8,5 12,2 21,4 18,1 15,7 ( 5,8) [6,8] 15,4 14,6<br />
1962163 - 14,4 6,2 9,6 8,6 . - -. - [3,9] 9,0 8,01<br />
Mittel ale Mean<br />
1956/57-1961/62<br />
9,9 13,1 19,5 15,9 11,2 9,6 5,1 13,9<br />
_<br />
Salmon per 100 nets<br />
1955/56 ( 8 ,9) 8,5 8,7 14,0 1<br />
1956/57 8,2 ( 7,3) 7,9 5,6 7,1 7,8<br />
1957/58 « [ 3,01 14,2 8,6 6,5 9,0 8,6<br />
1958/59 (20,8) 29,7 12,0 4,6 4,6 10,5 15,4<br />
1959/60 ( 3 , 3 ) 10,6 8,3 5,0 4,4 5,9 8,0<br />
1960/61 11,3 8,8 11,8 5,7 •( 8,4) 15,2 5,7 5,7 1,7 8,2 8,9<br />
1961/62 8,1 10,5 11,4 (11,4) 17,4 11,9 12,6 4,5 7,1 5,1 8,6 9,7<br />
1962/63 2,4 3,8 4,9 - - - --. - 7,4 5,7 2,5 5,7 12,0 1<br />
13,1 10,0<br />
' 11,6 8,6 12,9 13,6 9,2 . 5,1 4,4<br />
9,7 ___<br />
•<br />
6,1 4,9 9,7<br />
1 Values determiined•with the. aid of the mean monthly trend.<br />
Figures' in .0 are based on the catch of 100 to 200 salmon, those in [] are based on catches of less<br />
thgn 100 . salmon, plain figures are based on the catch of more than 200 salmon.<br />
II-Iv<br />
•
• to lower figures than in the fall.<br />
•<br />
20<br />
10<br />
•<br />
x-- — x A Glowinska, J PlecAura,1961'<br />
• — • deutsche Messung,L959<br />
German.measurement.<br />
31 411111<br />
It is a well-known fact that salmon are cold-stenothermal fish.<br />
G. Alm (1958) has pointed out that there is a critical temperature that<br />
determines the beginning and the end of the fishing season. According to<br />
this, salmon seek out deeper water layers when the temperature at the sur-<br />
face exceeds 11 to 12 ° C. They return to the surface water when its tem-<br />
perature has dropped to 11 to 12 °C. Alm, however, estaaished that this<br />
rule holds only for such fish who are on migration for food. On the other<br />
hand, those on spawning migrations ascend the rivers in water temperatures<br />
of up to 17 ° C.<br />
According to our measurements and according to Polish meas-<br />
urements in the D4ig Deep (A. Glowinska 1961, J. Piechura 1961) the sur-<br />
face temperature drops during October below 12 ° C and rises in June to<br />
over 11 ° C. The course of the temperature curve in Fig. 7 coincides with<br />
oc<br />
oberedcher, Surface<br />
t was.serterperatur water temperature<br />
• monaielgonths.<br />
Fig. 7. Temperature conditions in the Danzig Deep. ,<br />
the increase in the captures per unit effort until Decembei HoWever,<br />
are caught already in August, when the surface temperature is above 17 ° C<br />
and in September also at about 14 ° C. Without doubt, at that time manY fish<br />
[p. 242]<br />
salmon<br />
* still keep to the depths. On the other hand, the best catches were obtained
only in December or even in January. It is thus possible that further fish<br />
did still rise steadily from the deeper layers of the water. With such a<br />
fluid transition it is perhaps not correCt to speak of a critical ;tern-<br />
core..k.es<br />
perature. To judge by the size of the-cep-tuxes per unit effort, only about<br />
one-half of all fish have returned to the surface in October, when a tem-<br />
perature of about 10 ° C prevails there.<br />
tC<br />
Further changes in the captur -e-s per unit effort are not correl-•<br />
ated with the course of temperature. Beginning in March (for line catches<br />
already beginning in February), when the temperature is lowest, the yields<br />
are already dropping again. The salmon season comes close to its end at<br />
. the beginning of June, when the surface temperature passes 10 ° C.<br />
As regards an explanation for the reduction in values for the<br />
ccutclee<br />
-cap:tee:re-8 per unit effort during February/March, we are reduced to assump-<br />
tions. There is the possibility that temperatures of from 2 ° to 8 °C cons-<br />
titute an optimum range for salmon. The area of its habitat lies in the<br />
[P. 243]<br />
summer probably under the layer of the temperature discontinuity (at a<br />
depth of 25 to 50 m), where the temperature is 2 ° to 3 ° C. It must be as-<br />
sumed that the fish do not dwell in still greater depths, because in the<br />
bottom layers of tlie large basin of the Baltic Sea there is an occasional<br />
lack of oxygen and sulfuretted hydrogen may be present. (Salmon need a<br />
minimum of 5 mg 02/1.) If thé fish wish to escape from water that is too<br />
cold in February/March, they will have to pass through the layer of dis-<br />
continuity, which at that time lies at a depth of 60 to 70 m. Below this<br />
the temperature is about 5 ° C. (A. GloWinska 1961, J. Piechura 19 6 1)<br />
HoweVer, this question Of behaviour is at the môment not<br />
ecdeiter,<br />
decisive for us; because the question is in how far the eaptueee per<br />
unit effort as expression for the stock density are infltlenced by other<br />
32
•<br />
•<br />
Umfang = Cire umference<br />
- 33 -<br />
factors during the season. We can say with certainty that the highest<br />
values that appear in December and January (line catches) or also in<br />
February (net fishing) represent best the stock density. Lower values<br />
during the fall may be attributed to the temperature conditions, because<br />
cd.-Éke,s<br />
the salmon return only gradually to the surface. The dropping -c-ap-tur-es ,<br />
per unit effort in February/March do not reflect with certainty the strength<br />
of the stock.<br />
The question is now in what manner would it be possible to<br />
cad,<br />
obtain an average value for the -capture per unit effort during a season<br />
that would represent best the density of the stock. In the first place,<br />
the highest values of each season might be considered to be representative.<br />
It is, however, not necessaryfor us to use exactly these statements. The<br />
et„.teite5<br />
decisive demand that must be made of the captures per unit effort is that<br />
they should be directly Comparable from season to season. In regard to the<br />
line fishery we can, for examPle, compare the December values of the years<br />
1956 to 1958 with one another, which brought the highest :captures per unit<br />
effort of each fishing season. The result for December 1960 can, however,<br />
not be included in this comparison because the highest value of this season<br />
Cm<br />
so<br />
ne • 745<br />
Liirg .e = Length<br />
. ,<br />
.<br />
Fig. 8. Relation between total length and circumference in<br />
the salmon (the curve has been drawn with the aid of ,<br />
.<br />
group aVerages).<br />
en1 .
was obtained in January.<br />
- 34 -<br />
The individual values for each month from NOvember . till January<br />
axe based in general on the catch of more than 1000 salmon. In order to<br />
exclude accidental changes in the catch as far as possible, it.would be<br />
c cute-k-<br />
suitable to calculate the represntative capture per unit effort for each<br />
season as the arithmetical mean of these three months.<br />
This applies, however, only to the line fishery; but we must<br />
compare these statements also with the net catches in regard to their<br />
value as indicators for the strength of the stock.<br />
In theinvesegation of the selection effect of hooks it could<br />
be shown that hooks of opening 19 mm did not have a mechanically conditioned<br />
selective effect in comparison with those of 13.5 eening. We can therefore<br />
Ceckes<br />
assume that the -cupttures per unit effort by line are hardly affected by<br />
selection. This, however, does in no case apply to the net catches. If We<br />
select a Mesh of 80 mm, this would correspond to a periphery of 320 mm of<br />
the fish to be taken. According to Fig. 8 such fish have a length of about<br />
73 cm. All fish that are staller than 73 cm, Or that have a circpmference<br />
of under 320 mm have thus the chance to slip through the meshes. Let us<br />
._now examine in contrast to this the selective effects on the larger fish.<br />
In Fig. 9 the circumference of the body in different regions has been en,<br />
tered. It is found that there are indentations in the region of the eyes<br />
• and the gill covers, by which . the salmon can be retained in a mesh of the<br />
gill net. In addition, a part of the submaxillaries protrudes . à the end of<br />
thé mouth opening at the height of the eyes. These extensions act in rel-<br />
ation to the mesh of the net as a barb. One can therefore say that the-<br />
. -body circumference in the region between the eyes*and nape is decisive for<br />
selection. A circumference of the head of 320 mm in the region of the eyes<br />
P. 244]
•<br />
- 35 -<br />
and nape corresponds to a total length of 91 to 112 cm. Furthermore,<br />
small as we ll as large fish, who are not retained by the net on account<br />
of the body circumference, can become entangled in the net by their teeth<br />
and may be captured in this manner.<br />
According to what has just been said, one cannot expect a com-<br />
plete selection for small as well as for very large fish ., whereas for a<br />
mesh of 80 mm the highest selection can take place for lengths of between<br />
about 74 cm and 92 to 112 cm.<br />
In practice there are certain differences in selection that<br />
depend on the material of the nets. It has already been mentioned that<br />
the heavy hempen nets are not as effective as perlon nets (Table 2). In<br />
a net of gynthetic fibres even those fish can still become entangled whose<br />
circumferenOe at the head is greater than the mesh sise, since some of<br />
them can become entangled in the thin net material, or become àtuck in the<br />
fine yarn with their teeth.<br />
Table 8. Selectivity of salmon driftnets with an average<br />
mesh of 78.75 mm.<br />
1 2 3 4 5<br />
Total Number of salmon Net catch Tripartite Value of column 4<br />
length Hook, Net Line catch adjustment when 7.5817 100<br />
cm<br />
52,5 ' 6<br />
57,5 7 0,1895 2,50<br />
62,5 31 17 0,5484 0,4038 5,32<br />
67,5 92 61 0,6630 0,9607 12,67<br />
72,5 82 137 1,6707 1,9969 26,33<br />
77,5 35 128 3,6571 2,9759 39,21<br />
82,5 20 . 72 3,6000 5,7267 75,50<br />
87,5 13 129 9,9231 7,1991} 94,85<br />
92,5 , 27 218 8,0741 8,4824 0 7,5817 111,90<br />
97,5 20 149 7,4500 7,0636 93,08<br />
102,5 6 34 5,6667 4,8722 64,25<br />
107,5 2 3 1,5000 2,3889 31,50<br />
112,5 1 0,5000 6,59<br />
341 949
Hempen nets are nowno longer used in the German salmon fishery.<br />
For this reason we are using as basis for the present investigations the<br />
mesh widths of the synthetic nets. The measuring of the mesh of 24 nets<br />
on four cutters gave an average mesh width 2 of 78.75 mm (mesh opening<br />
about 157 mm).<br />
Ldnge<br />
CirCUmYerence<br />
A . eye<br />
D insertion of dorsal fin<br />
N .= nape -<br />
0 = operculum<br />
S = snout<br />
36<br />
• For the determination of the<br />
selectivity of gill nets the catches<br />
with driftlines can be used by way of<br />
comparison. For this purpose I have<br />
line catches of 341 fish and net catches<br />
of 949 fish, for January 1964 from the<br />
Danzig Deep (Table 8). If one calculates<br />
for the groups of length the ratio of<br />
values in the range 85 to 99 cm. If one<br />
Fig. 9. Relation between total<br />
length and circumference in four P uts the mean value of this range equal<br />
salmon.<br />
to 100, one obtains then the percentage<br />
selectivity for the individual groups of length (Table 8, column 5).<br />
P. 245]<br />
the number of netted salmon to the number<br />
of lined salmon, one obtains the highest<br />
O. Christensen (1963) has carried out these investigations with<br />
[p. 246 ]<br />
the aid of Danish net catches and line catches in March 1963. The selec- • '<br />
tivity curves for the two investigations are shown in Fig. 10. It is seen<br />
that the German nets select larger salmon than do the Danish nets.<br />
Only a few large fish escape from the nets, but a substantial<br />
2 Mesh width = distance between the centre of one knot and. the Centre cf the<br />
next; mesh . opening . length of the stretched mesh.
•<br />
• /<br />
100<br />
50<br />
Selektion Selection<br />
/ I<br />
/<br />
/ •<br />
:- 37 -<br />
part of small salmon.can slip through the meshes. Correspondingly, the<br />
50-per cent lengths 3 of the Danish curve are lying lover than those of<br />
the German curve. They amount to about 68 cm or 78 cm, respectively, for<br />
small salmon and 100 cm or 105 cm, respectively, for large salmon.<br />
dânische Netze — - Danish nets<br />
—deutsche Netze (78,75rnm np„rman nets<br />
schenwene<br />
Mésh width<br />
0 0 100 uo cn,<br />
. mowin g.= Total length<br />
.. . .. .. . .<br />
Fig. 10. Selectivity curves for salmon driftnets.<br />
Let us return to the object of our investigation, that is,<br />
obtain comparable data for the density of the stock. The -egelliam e per<br />
unit effort of the driftnet fishery are, to be sure, not representative<br />
in regard to the age composition of the stock being fished. They are,<br />
however, comparable among themselves, if.the mesh width of the nets used<br />
remains constant and if there are no differences in growth. They can<br />
therefore be used as a . measure for the population density.<br />
It can also be stated that the comparability of the<br />
.per unit .effort by line as well as by net sis i not being influenced by the<br />
selective effect.<br />
•<br />
ce-<br />
However, the two kinds of gear differ in one substantial Point.<br />
3 Fifty percent of all salmon.(of a certain group of lengths),.that meet<br />
the net as Potential objects to be caught, - are retained in the net..
Number of sprat<br />
Season Oct./Nov. Dec./Jan. Feb./March /cutter/day<br />
8Pring, Danzig Deep<br />
• 1956/57<br />
1957/58<br />
1958/59<br />
, 1959/60<br />
' 1960/61 937<br />
1961/62 1 057<br />
1962/63 519 •<br />
453 11 681<br />
" 1830 82 407<br />
1 383 55 385<br />
1 302 8 1001'<br />
554<br />
728<br />
2 1 400<br />
1 042 r<br />
11600'<br />
4 2001<br />
2 1001<br />
- 38 -<br />
The ddftnet works entirely passively, whereas the driftline attracts the •<br />
salmon by the.bait. Spice the fish pureue also the naturally occurring<br />
food fish, there is competiticin between the artificial and natural offer<br />
of food. If we assume that the population density N and the intensity of<br />
fishing f (that is, the artificial offer of food through bait) are constant<br />
in the years x and x + 1, whereas the natural food fish are present in the<br />
strength p and 0.5 p, respectively. That obviously means that drift-line<br />
catches must increase'in the year x + 1. In contrast to this, the catches<br />
with driftnets remain the sanie in both years. In other words: if in the<br />
year x the • catch by 1000 hooks equals the catch . by 100 nets, then the catch<br />
. by 1000 hooks in the year x +1 is greater than the catch by . 100 nets. When<br />
cate,h-<br />
our investigations show such changes; then we have to reckon that.emeimae<br />
per unit of effort by line is influenced by the ratio between the natural<br />
[p. 247]<br />
and artificial food offer.<br />
Table 9. Number of hooks, which were required during<br />
different fishing periods to equal the catch results<br />
of 100 nets. (Calculated with the simple. Means<br />
. of Table 7.)<br />
1 The data were kindly supPlied by Dr. J. Elwertowski (Institute for<br />
' Ocean FisherY, Gdynia) as. catch in kg per outter . and day. The recalculation:is<br />
based on an average weight per sprat of 9.33 g (P.<br />
F. Meyer-Waarden 1942), all other statements -after J. .Eawertoweki'<br />
1959.
- 39 -<br />
In Table 9 have been calculated the numbers of hooks that were<br />
required in order to equal the catch per 100 nets on the basis of the cep -<br />
-e unit of effort of sprat (dragnet) by Polinh cutters in the Danzig<br />
Deep (Elwertowski 1959), since sprat are considered to be the most impor-<br />
tant food fish of salmon (see Table 48).<br />
The number of hooks required and the catches per unit of effort<br />
of sprat in the Danzig Deep show a very good agreement for the three catching<br />
periods 1956/7 to 1958/9. During the subsequent years a considerable decline<br />
of the sprat catches took place. Elwertowski (1964) has pointed out that the<br />
availability of sprat in winter depends on the temperature conditions. Eel-<br />
atively cold water delays the time of spawning and therewith the concen-<br />
tration of the sprat into pre-spawning and spawning swarms. It is therefore .<br />
possible that in the years in question only the availability of these fish has<br />
declined, whereas they were still available as food for the salmon. For the<br />
fishing. seasons 1959/60 to 1961/2 we obtain .therefore a new ratio between<br />
the number of the hooks required and the captures per unit àf effort,of<br />
sprat. According to these statements it is not possible to eiclude the pos-<br />
sibility that changes in the dênsite of the stock of sprat can effect. the<br />
line catches of salmon in the spring.<br />
There are only verY few comparable values available for the fall<br />
and winter months. The compa#son betweeen the number of hooka and nets<br />
. that are required for a certain,catch result of salmon, appears at this<br />
time to le much more favourable for the driftlines. It suggestà itself,.<br />
that this fact is due to the scarcity of sprat, because the sprat appear<br />
only in spring iâ larger numbers in the upper layers.of thewater. (see<br />
011apter 6.4w). Annual differences - cannot be demOnstrated..<br />
It has been investigated in how far otherfactOrs than the
-4o-<br />
stock density can affect the catches per unit effort with driftlines and<br />
driftnets. Hitherto internal (selection) and external (temperature and<br />
food) causes have been discussed. Now we shall investigate a further ex-<br />
ternal factor, namely the effect of the wind.<br />
cecÂd.!..<br />
In Table 10 the eep-teres per unit effort with hooks in various<br />
fishing regions4 under different wind slpeeds and wind directions have been<br />
assembled. The figures from fishing region 5 are based mainly on catches<br />
of from 200 to 2000 salkon, those from the other fishing regions are based<br />
on from 20 to 300 salmon. Unreliable data are given in Q.<br />
The best catches in all fishing regions have thus been made under<br />
stronger winds. Before we can test the significance of the differences in<br />
the catches, we shall have to consider that the values of columns 7 and 8<br />
(Table 10) did not originate in a uniform system. We have started from the<br />
ceckes<br />
basis that the ceetutaee per unit effort should serve as a measure for the<br />
strength of the stock. When we now investigate the effect of the wind, it<br />
can be established at once that variations in the strength in different<br />
years can produce perhaps far greater variations than the effect of the<br />
wind. Effects of the food supply and of the temperature conditions have<br />
been demonstrated above and it is not impossible that still other factors<br />
influence the size of the capture per unit effort. •<br />
These deviations increase the scatter of the series that also<br />
enters as a variable into the test equation.,In order to eliminate the<br />
effect of the strengths.of the different year classes, the deviations of<br />
the Values in column 8 from thogeof column 7 as percentages were used as<br />
the Iasis for the test of significance.'<br />
4 For the fishing regions see Fig. 6.<br />
-
. Table 10. Number of salmon per 1000 hooks in dependence on the fishing grounds<br />
and wind directions (weighted means).<br />
(For fishing grounds see Fig. 6.)<br />
1 ' • 2 3 4 5 6 7 8 9<br />
- Fishing Time of Weighted Total«<br />
‹z 5 Beaufort >5 Beaufort<br />
ground Season capture<br />
Calm mean weighted<br />
S W N E S W N E var. 5 B . mean<br />
Simple mean<br />
Simple mean<br />
Signifik eu wert Value of significance f 000<br />
fur<br />
54 for differences. -<br />
amone catches.. Der cent .<br />
le<br />
81<br />
1,15<br />
68<br />
Simple mean<br />
0.1111%<br />
.. _ - ..<br />
1956/57.. X • 5,0 11,1 0,0 14,6 17,6 27,4 ' 9,9 21,8 13,2<br />
1957/58 . -X-I 11,1 21,4 . - • 14,3 15,4 . 7,8 11,5 14,6 12,5<br />
1958/59 ' X-I 14,2 4,7 55,7 33,0 85,7 4,4 «<br />
22,4 19,3 20,9<br />
1959/60 • X-II . . 11,7 7,0 . 4,1 16,6 18,3 35,8 14,2 7,3 19,2 11,9<br />
1960/61 X-XI ' 6,5 . 8,9 10,1 9,7 5,8 • 15,9 8,9 • 14,6 11,4<br />
1961/62 X-XI 7,6 10,9 10,6 11,5 10,9 12,5 6,4 14,2 9,0 - 10,7 9,7<br />
1962/63 VII I-X 7,9 '. - 4,1 . 14,4 5,2 8,6 7,6 12,3 5,3 - . 6,1 • 8,9 - 8,1<br />
8,8 8,2 18,5 9,2 15,8 26,0 8,9 19,7 11,0 10,7 15,6 12,5<br />
,<br />
SignifiLmvwert t Value of significance f 3,02<br />
für Fangdifferenzeni °/o for differences among catches per cent<br />
97,5<br />
1954/55 XI-III 15,5 12,9 14,2 19,3 15,8 13,9 15,0 3,3 14,4 15,2 14,6<br />
1955/56 XI-V 7,2 7,0 7,6 17,7 19,7 11,2 13,4 20,1 4,9 8,9 15,7 11,2<br />
1956/57 X-V 16,0 19,7 26,3 15,5 29,2 32,9 21,3 23,6 18,1 20,3 29,1 23,0<br />
1957/58 X-I V 11,4 10,2 13,0 8,1 17,9 15,4 6,9 24,6 8,8 10,2 14,3 11,6<br />
1958/59 X-IV 11,4 14,3 12,3 13,2 23,1 37,8 33,2 18,8 12,3 13,2 33,7 18,5<br />
1959/60 X-I I I 9,0 8,7 8,0 8,5 10,8 7,6 8,7 10,1 7,2 8,7 9,9 8,9<br />
1960/61 XI-III 12,0 19,0 10,2 8,5 11,4 11,7 19,8 10,0 8,0 11,5 13,2 12,0<br />
1961/62 XI-IV 14,5 17,4 15,3 11,4 15,2 30,1 16,3 13,7 4,3 15,4 20,3 1 7,3<br />
X-V 9,1 8,5 9,1 7,1 9,9 9,0 7,0 16,1 8,6 9,1 8,8 1962/63<br />
X-IV 11,8 13,1 12,9 12,2 17,2 19,1 16,7 15,9 9,2 12,4 17,9 14,0<br />
1956/57 X 10,2 11,0 - 12,9 8,5 21,7 26,8 21,3 4,9 10,4 24,9 11,8<br />
I<br />
1957/58 X-I 9,2 8,6 5,6 4,1 9,5 8,1 7,3 10,3 8,4 8,5 8,4<br />
1958/59 XI-11 6,3 7,0 11,0 22,3 18,6 13,7 12,0 18,6 12,5<br />
6 1959/60 X-I V 5,4 7,9 4,7 7,9 3,9 15,6 9,8 3,6 6,0 9,9 6,8 t<br />
1960.'61 X-I 4,7 10,0 - 11,4 7,1 13,8 12,8 9,0 13,8 9,3<br />
1961/62 XI-III 6,9 5,6 9,2 7,4 6,7 13,0 16,7 7,2 15,5 10,6<br />
1962/63 XI-IV 6,6 11,4 4,5 . 11,3 10,4 10,6 8,3 16,2 8,5 9,8 12,1 10,5<br />
• 7,1 8,8 .8,5 1 0, 8 12,1 12,7 13,4 12,5 9,0 9,0 14,8 10,0<br />
_<br />
3,53<br />
ignifiltriztvert<br />
für Fang di fferenzenl<br />
t<br />
c1 /<br />
Value te significance t<br />
for differences among catches per cent 99,1 NI<br />
1 Zwisdlen deri Einheitsanen < tmd > 5 Bnuftirt..« Be twe e n the catches pér unit effort -. -2 - .and >5 Beaufort<br />
2,63<br />
97,1<br />
r-n<br />
.<br />
-P.<br />
Ce
- 42 -<br />
In this manner were obtained the values of significance in Table<br />
[P. 249]<br />
10. Since W (t) equals 0.05 for all.fishing regions, we have here very<br />
probably genuine differences in the catch. It is possible that they stand<br />
in the majority of cases in relation to the wind speed. .<br />
• The results for the net fishery (Table 11) have an entirely<br />
different aspect. For the fishing region 5 better catche s. were recorded<br />
for lower wind 'speeds. The probability that this concerns genuine differ-<br />
ences in the catchis 97.6 per cent. In the other fishing regions also the<br />
values are higher for winds under 4 on the Beaufort scale than for stronger<br />
winds. No test for significance was made, because only few individual•<br />
values are available for strong winds, which are based mostly on catches<br />
of fewer than 100 salmon. The material on hand, however, gives the impres-<br />
sion that differences in yield that are probably caused by wind can be dem-<br />
onstrated for all fishing regions in the Baltic Sea proper.<br />
Before the possible causes for this phenomenon are considered,<br />
we shall first examine the relation between wind direction and yield of<br />
catch. At winds of less than 5 on the Beaufort scale it is nôt possible<br />
to demonstrate significant differences in line catches in relation to<br />
wind direction. For wind speeds above 5.13eaufort only fishing region 5 can<br />
be investigated, because there are too few values for the other regions.<br />
The test for significance with the data of column 5 was carried out by con-<br />
sidering the deviationà of the yields for west wind against those for east '<br />
wind; as Well as the values for north and south winds. The•probability that<br />
the catch differences are significant amounts to 81 per cent concerning<br />
north wind catches, to 68 per cent in regard to east wind catches and 54<br />
per cent for south wfnd catches. The differendes are thus not significant.<br />
At the other fishing grounds . the , west wind catches are• greater for '
• Table 11. Number of salmon per.100 nets in dependence on fishing grounds and wind directions<br />
(weighted means).<br />
• (For fishing grounds see Fig. 6.)<br />
1 2 3<br />
Simple mean<br />
4 5 6 7 6 9<br />
Fishing Time of ..c. 4 Beaufort Calm ..-,..4 Beaufort • Total .<br />
ground season capture .S W N E • var. S W N E Weighted weighted<br />
mean mean<br />
12,3 9,7 6,1 5,6- 6,3 10,2 1 6,3 9,3 -<br />
.4 1961/62 VIII-XI, III-V 7,2 6,5 13,6 8,2 12,3 6,3 1,2 5,4 8,1 • 6,8 7,4<br />
1962/63 VIII-X 2,2 4,9 5,1 3,7 4,7 3,6 4,5 5,0 3,1 5.13,8 4,3 3,9<br />
. .<br />
. . • - .<br />
,<br />
6,2 5,7 . 9,4 8,1 7,2 7,3 . 5,4 - 3,9 ' 5,0 7,4 . • 5,8 6,9 •<br />
Simple mean<br />
.... .. . iii-iv<br />
. . , .<br />
1955/56 I V-V 5,0 9,6 9,2 8,4 9,0 .. ' - 12,9 . . . - se 5,3 8,7 :<br />
1956/57 II-V . 5,3 7,0 5,7 -7,1 8,6 ' . 5,6 .5,6 ; 2,3 7,3 ' 5,1 6,9..<br />
1957/58 III-V - 7,4 7,3 12,0 14,7 8,1 ". 5,4 3,0 3,4 9,1 - . .4,1 . 8,9<br />
• 1958/59 XI-V 13,3 8,8 8,2 _ 7,3 12,8 8,3 , . 3,1 2,7 . - • . 11,0. . 3,5 .10,8,<br />
5<br />
• 1959160 II-VI 10,9 7,6 5,6 6,0 6,2 . 6;7 - 1,8 5,3.. 7,1 . 6,5 ' 5,7 6,4<br />
1960/61 XI-V 7,3 . 10,8 7,4 2,2 6,1 . 11,0 11,9 1,7 " 1,6 7,2 10,5 . 8,0 .<br />
1961/62 XI-VI . 9,1 7,7 7,2 7,2 7,6"" 3,3 8,1 3,2 11,2 . 8,1 - 5,7 7,7<br />
. • 1962/63 IIPVI 6,2 -5,7 7,6 - 4,8 . 4,3 4,1 - 5,6 4,3 2,9, . 5,8 - 3,9 5,6 .<br />
S imp 1 e mean<br />
Il-V 8,1 8 ,1 7,9 7,2 7,8 6,7 5,9 4,8 4,7 8,0 5,5 7,9<br />
- Signifikanzwert t • Value of significance 5 t<br />
fiir Fangdifferenzen 0/0 for differences among catches per cent<br />
3,06<br />
98,2 .<br />
1956/57 III-IV 7,5 4,0 11,9 . 8,3 4,4 6,4 7,3 0,8<br />
1957/58 V 4,7 4,7 4,7<br />
1958/59 III-IV 7,3 3,6 2,8 6,9 6,1 6,1 .<br />
6 1959/60 III-IV 3,8 3,9 5,2 3,7 6,3 6,6 3,6 3,8 4,7 4,2<br />
1960/61 XI I-I, III-V 3,8 1,7 6,7 4,4 1,5 • 3,0 1,5 2,8<br />
1<br />
1961/62 I-IV 9,0 8,6 ' 6,5 125,0 20,7 12,7 5,7 7,4 19,8 7,1 18,3 -<br />
1962/63 IX-V 4,5 '10,8 16,5 6,1 7,9 - .<br />
2,5 10,0 5,9 9,8 4›.<br />
te+<br />
I-1V<br />
6,0 4,9 6,4 31,3 10,0 7,9 10,5 4,6 4,5 7,7 5,3 7,5<br />
•
- 44 -<br />
winds over 5 Beaufort. However, this cannot be demonstrated for net catches<br />
during winds of less than 4 Beaufort. For yields ut over 4 Beaufort there<br />
are too few data.<br />
•By<br />
way of summary it can be said: with strong winds one obtains<br />
better line catches but poorer net catches than with weak winds. West winds<br />
over 5 Beaufort bring better line catches on the fishing ground 5 than<br />
winds from north and east. •<br />
It suggests itself to explain these results in the following<br />
manner: with strong winds and a correspondingly rough sea the hooks are<br />
moving up and down to a considerable extent. The salmon recognize the<br />
[P. 251]<br />
bait sooner than during a weak sea way. The good yields during west winds<br />
appear only with winds of over 5 Beaufort. This suggests the assumption<br />
that it is not the wind by itself but a current generated by the wind that<br />
affects the yields. This explains at the saine time the smaller net catches<br />
that are found during strong winds. The sheet of the net is no longer<br />
tightly stretched during a heavy sea way and strong currents and thus is<br />
less efficient than during calm weather. The - individual values of column<br />
5 give the appearance that in the open ocean (fishing grounds 4 and 6)<br />
the catch is better during north and east winds; in the DanZig Bay, however,<br />
it is better with west winds.<br />
On the basis of these findings one has to reckon with the fact<br />
cek es •<br />
that the strength of the wind can influence substantially the eap4ueee per<br />
unit effort by driftnets and driftlines. At the fishing ground 5 (Table 10)<br />
there were caught on an average during the years 1954/5 to. 1962/3 5.6 more<br />
salmon during strong winds than.during:light winds. Weather with predom-<br />
inantly strong winds can thus exert-a considerable influence on the yields.<br />
•
•<br />
- 45 -<br />
cza-ci, es<br />
When considering the eaptlaTee per unit effort as indicators of the stock<br />
density it will be necessary to-take. into account the predominating<br />
strength of the wind.<br />
Certain differences in yield on the individual fishing grounds<br />
have already been indicated. The statistical treatment of .the figures>in<br />
column 8 (Table 10) shows that the differences between 14.0 (fishing ground<br />
5) and 10.0 (fishing ground 6) are significant at 90 per cent and between<br />
14.0 and 12.5 (fishing ground 4) at only 66 per cent. Fishing was carried<br />
out during the entire season on the fishing grounds 5 and 6, whereas on<br />
the fishing ground 4 fishing was carried out predominantly between October<br />
and December. With regard to this fact, it can be seen that the fish were<br />
probably not uniformly distributed over the entire area.<br />
It is astonishing that these differences on different fishing<br />
grounds can be demonstrated during a succession of years. Unfortunately,<br />
the data for the net catches are not sufficient for the investigation of .<br />
this problem. It can thus not be clarified unambiguously whether the dev-<br />
iations that are connected with the fishing ground are caused by differences<br />
[13.252]<br />
in the population density or by differences in the behaviour of the salmon<br />
in regard to the twe kinds of gear.<br />
catrel.e.s<br />
In the critical treatment of the data for the eeetAkre-e-per<br />
unit effort it is necessary to mention the local movements as a form of<br />
salmon migration (see 4.2.). Hitherto the answer to the question whether<br />
eeech<br />
a tap4uee per unit effort is to be considered as representative has been<br />
made in relation to the number of salmon that form the basis of the<br />
values. However, sometimes very large assemblies of salmon take place<br />
ccotei.es<br />
that send the enp4mees per unit effort soaring upWards tenfold. These<br />
values are then based on .a very large number of salmon. However, they do
20<br />
10<br />
Number of ealmon/1000 hoOks<br />
Mean Denmark<br />
0-6 Mittel 1958/59-1962/63 Danemark<br />
Mittel 1956/574961/62 Dtutschland<br />
Mean Germany<br />
"D et- .15-A r.1 F13 x Morale us Months<br />
Fig. 11. Monthly means for the Danish and German cap-es<br />
per unit effort in driftline fishing, Danish values.<br />
(After O. Christensen 19 6 3, 19 64.)<br />
not give the average density of the stock. In general, the effect of such<br />
happenings on the value of the annual average is, - however, very smell,<br />
because it is largely compensated for when forming the average value.<br />
The evaluation of the captures per unit value will be concluded<br />
with a comparison of the data for . different countries.<br />
In Fig. 11 is presented the course of the monthly values of the<br />
captures per unit effort in the Danish5 and in the German driftline fishery.<br />
ct.tc.I.es<br />
The two Curves show a different course. The Danish earobures. per unit effort<br />
show the theoretically expected temperature.dependent steady rise until<br />
February and after that a sudden slump. In contrast to this, the German<br />
values rise quickly until December and drop slowly dûring the following<br />
months.<br />
33.<br />
5 Personal - communication from O. Christensen.<br />
„
- 47 -<br />
If We examine once more the factors investigated hitherto that<br />
can cause short-term fluctuations, we have to state that the effects of<br />
temperature and the influence of selection cannot be responsible for these<br />
differences. The two causes, food supply and wind conditions, could play<br />
a role only if the two fleets did their main fishing during February on<br />
different fishing grounds. To this question the monthly yields on the in-<br />
dividual fishing grounds (Tables 12 and 13) furnish an indication.<br />
cAtekes<br />
The monthly values of the Danig„h 'captures per unit effort in<br />
1962/3 on the fishing grounds 4 and 5/6 show twO clear maxima, in November<br />
and in February (0.Christensen 1963). The difference between the two is<br />
eight salmon on fishing ground 4, only two', however, on fishing grounds<br />
5 and 6.-<br />
et...tees<br />
The German ea-pturee per unit effort show on the average not two<br />
maxima for the fishing seasons 1957/8 to 1961/2, but the highest yields<br />
occur on the fishing grounds 4 and 6 in January instead of December. These<br />
differences indicate the possibility that the different monthly courses of<br />
the Danish and German captures per unit effort by line are dependent on<br />
the fishing grounds.<br />
Table 12. Number of salmon per 1000 hooks on different<br />
fishing grounds, according to Danish catches 1962/3.<br />
(0. Christensen 1963.)<br />
Fishing ' Months<br />
grotind XIII IX X XI - XII I II III IV<br />
. .. ...<br />
- • - • • • • .<br />
2 6 5 11. 10 9 .<br />
3 5 6 13 15 14<br />
4 - 5 . 9 11 . : 14 10 13 . 22 11 ..<br />
5/6 . 9 8 16 lb • 14 18 ' 14 ' 4<br />
5 • 8 ' 11 14 11 13 19 14 • 4<br />
Total<br />
There is a further difference between the Danish and German<br />
[P. 253]<br />
,
• ceckes<br />
- 48 -<br />
captuelee per unit effort that has to be pointed out (Table 14). The Danish<br />
line catches are higher on the average and the net catches slightly lower<br />
than the German results. It has already been said that on the German cutters<br />
Table 13. Number of salmon per 1000<br />
hooks on different fishing grounds<br />
the taking up of the lines begins<br />
according to German catches 1957/5 8<br />
to 1961/62.<br />
already in the forenoon; whereas<br />
the Danish fishermen begin this in<br />
Fishing Month general -in the afternoon. The longer<br />
ground XI XII I II<br />
fishing time appears thus to result<br />
4 11,1 18,6 18,9 3,1<br />
5 12,0 19,6 14,0 10,1 in better yields.<br />
6 6,6 9,7 10,8 7,7<br />
On the other hand, hempen<br />
nets are still being used in Denmark. Furthermore, the driftnet fishery<br />
is there carried out prepcinderantly in the spring months. In contrast, .the<br />
eceekes<br />
Table 14. Cmptuees per unit effort in Denmark<br />
(0. Christensen 1963), Sweden (G. Alm 1954a,<br />
1956- 61) and Germany.<br />
Season<br />
Number of salmon per 1000 hooks and 100 nets<br />
Denmark . Germany Sweden<br />
Hooks Nets Hooks Nets Hooks Nets<br />
1944/45<br />
38,2<br />
1945/46<br />
3 7,5<br />
1947/48<br />
1948/49<br />
1949/50<br />
1950/51<br />
1951/52<br />
1952/53<br />
1953/54<br />
1954/55<br />
1955/56<br />
1956/57<br />
1957/58<br />
1958/59<br />
1959/60<br />
1960/61<br />
1961/62 •<br />
-<br />
•<br />
17<br />
20<br />
11<br />
14<br />
16,5<br />
•<br />
• •<br />
9<br />
11<br />
6<br />
6<br />
5,4<br />
•<br />
' •<br />
' 14,0<br />
11,2<br />
18,9<br />
11,2<br />
17,9<br />
8,4<br />
11,6<br />
15,5<br />
. 8,7<br />
6,9 .<br />
9,0<br />
10,1<br />
5,8<br />
8,2<br />
8,8<br />
25,1 1946/47<br />
21,2<br />
24,2<br />
32,2<br />
30,0<br />
29,9<br />
29,0<br />
27,2 '<br />
41,6<br />
37,9<br />
17,2<br />
8,5<br />
7,7<br />
4,4<br />
4,9<br />
6,6<br />
12,9<br />
9,8<br />
6,4<br />
6,9<br />
• 5,4<br />
6,7<br />
4,5<br />
1962/63 11,9 5,7 9,0 5,7<br />
Durchsdulitt = Art ■-ragc<br />
1957/58-1962/63 1571 7,2 12,3 7,9<br />
- - • - - • - . • -
- 49 -<br />
German fishermen work during the entire year with synthetic nets. Since<br />
••<br />
the driftnet fishery gives better results in the winter months than in the<br />
spring, the difference for this gear alào finds an explanation.<br />
LID.254]<br />
If we now summarize the results of the critical examination of<br />
ctickes<br />
the data for the captures per unit effort, we see that we found four fac-<br />
tors than can influence in some way or other the yields of both kinds of<br />
fishing gear: local movements.of the salmon, fishing ground, water temper-<br />
ature, and wind condition. The significant differencesin yield on the dif-<br />
ferent fishing grounds are astonishing and their causes cannot<br />
be discovered unambiguously. It must be assumed that‘here two further fac7<br />
tors play a role, namely, the different distribution of the food fish as<br />
well as wind and current conditions. The rather rare local Movements will<br />
be eliMinated to a large extent through forming the average values. On ac-<br />
count of the quite uniform course of temperature in the different years,<br />
cercites<br />
the comparability of the captures per unit effort is preserved also in this<br />
* regard. However, the effect of the wind cannot be neglected.<br />
Two further factors influence in each case only the results of<br />
one kind of fishing geax. The supply of food affects the line catches, the<br />
selection affects the net catches. With constant mesh size and invariable<br />
growth conditions the net catches are comparable in spiteof their selective<br />
effects so that it will only be necessary to eliminate the effect of the<br />
food supply.<br />
•<br />
ceekes<br />
In the treatment of the effect of temperature on the eteturee<br />
per unit effort it had been arranged to calculate the average values of<br />
a season for the - line catches as the arithmetic mean for the months Nov',<br />
ember till January. After . the Danish and German values and their monthly<br />
-trend have beencompared ., it.now alipears appropriate to use the months<br />
•
- 50 -<br />
November to March for forming the mean value. Since sufficient data for<br />
driftnet fishing are available only from February onwards, it will be<br />
best to use the period February till April for the calculation of the<br />
representative carbtiee per unit effort.<br />
°led,<br />
An exact correction for the cap-titre-per unit effort by line<br />
in regard to the wind conditions could be made in the following manner.<br />
1. All data for each of the months November to March are to be divided<br />
into those for wind speeds above and below 5 Beaufort, and then sep-<br />
arated according to the four wind directions.<br />
2. It is possible to eliminate the wind effect by calculating the mean(Pf<br />
ç'th-<br />
the five data)for the wind directions and calm. This provides corrected<br />
values for each month above and below 5 Beaufort.<br />
3. A mean monthly value can be calculated from these data for the two<br />
wind speeds.<br />
4. The monthly trend of the melees per unit effôrt that is now available<br />
must be corrected in regard tb the food . supply through the comparison<br />
of net and line catches for the months February/March.<br />
5. Finally the arithmetic mean Of the data for the months November to<br />
March has to be calculated.<br />
When a complicated procedure of correction as —that outlined here<br />
Is to have any meaning, it will be necessary that the individual data menm<br />
tioned under point 1 are based on representative catches. Each of these<br />
statementà must have the same statistical value as the finally calcula,ted.<br />
yearly mean value. However, for the present material this does not hold<br />
true: The result of a correction as outlined above can . therefore be used<br />
only with reservations. '<br />
•<br />
To begin with, let us inspect first the net catches, which, it
•<br />
- 51 -<br />
is true, have to be corrected only in regard to the wind conditions. During<br />
the years 1955 to 1963 winds of over.4 Beaufort prevailed only on about 15<br />
per cent of all days with net catches. For safety reasons fewer nets were<br />
set on such days than on other days. Thus, if we neglect the results for<br />
wind speed of over 4 Beaufort, the correction for wind speed of the net<br />
catches has already been carried out. In order to eliminate a possible<br />
[p. 255]<br />
effect of the wind direction, every monthly value is formed as the simple<br />
mean of the data for the four wind directions and calm. The mean for the<br />
cz,tek<br />
months February to April represents then the eapturTe per unit effort of a<br />
season (Appendix, Table II). For 1956 and 1963 only results for April are<br />
'available, which havelben corrected with the aid of the average monthly<br />
trends (Table 7)..<br />
The monthly means for the line catches can be calculated accor-<br />
ding to the points 1 to 3 Of the above scheme. It is considered that a cor<br />
rectiOn for food sùpply of the available data would be out of place, be-<br />
cause the exact connection between line and net catches cannot be ascer-<br />
tained at present.<br />
In Table 15 have been entered the corrected net and line catches<br />
alongside the uncorrected:mean Values according to . Table 7. A àraphic<br />
presentation of the line catches shows that there is no correlation.iThe<br />
correlation coefficient is r 11 0.22 ± 0 .27 6 .<br />
According to the above discussions, we can indeed say that'the<br />
cate.e.e..s<br />
.-claria4zees Per unit effort by net have probably the smallest errors, we do<br />
not know, however, whether they can be considered to be representative for<br />
the entire season. Therefore, the data for the two kinds of gear offer<br />
only a support. The improved values that are being added annually will<br />
contribute to perfect Our knowledge of the extent of the stock of salmon
- 52-<br />
ce,.,td.es<br />
in the Baltic Sea. Later on we shall discuss the changes in the -eap-turen<br />
per unit effort as expression for the fluctuations in the stock.<br />
Table 15. Captures per unit effort of the German salmon<br />
fishery as expression of the strength of the exploited<br />
stock (percentages in parantheses).<br />
animal<br />
Number of salmon<br />
Season per 1000 hooks, XI-III per 100 nets, II-IV<br />
acc. to corrected acc. to corrected<br />
Table 7 Table 7<br />
1954/55 13,9 13 (85) .<br />
' 1955/56 11 8 (52) . 14 10 (102)<br />
' 1956/57 21,1 24,0 (157) 7,8 7,5 (77)<br />
1957/58 9,6 10,5 (69) 8,6 9,2 (94)<br />
1958/59 19,1 22,5 (147) 15,4 13,3 (136)<br />
1959/60 8,0 8,4 (55) • 8,0 10,5 (107)<br />
1960/61 10,5 10,8 (71) 8,9 . 8,5 (87)<br />
1961/62 14,6 15,8 (103) 9,7 10,0 (102)<br />
1962/63 8 8 (52) 12 8 (82)<br />
Dunfischilin . = Average<br />
56/57-61/62 15,3 = 100 9,8 = 100<br />
2.3.4. The yields of the salmon fishery<br />
The yields of the salmon fishery in the Baltic Sea have been<br />
ascertained according tontitements by G. Alm (1928a, 1954a), 0 . Christensen<br />
(19 6 1, 19 6 2, 1963), F. Chrzan - (1956b), E. lialme (pers. comm.), H. Hinking<br />
(190 5, 1913), R. Kândler (1957, 1958-63), A. Lindroth (1950), M. Linshev<br />
(1961), C. G. J. Petersen and A. Otterstrlim (1904), J. A. Sandmann (190e),<br />
S. J. Sjtigren (19 6 3),.F. Trybom (1910), and from the Bulletin Statitisque.<br />
(Vol. 1-45)(APpendix III).<br />
In the figures for the fishery in the Baltic Sea and in part<br />
[P. 25 6 ] -<br />
also in those for the river fishery are'included alsothe sea trout. The<br />
statements about their'share are incomplete. The yields of sea trout are<br />
summarized in Table V in the Appendix according to the available data and<br />
amounted,to about 100 to 400 t for the Baltic-Sea for<br />
some estimates. They
Table 16. Seasonal yields of the fishery for salmon...and sea trout in the Baltic Sea properl.<br />
Fishing • Danmark Germany Poland • Sweden Total<br />
period t Number t ' Number t Number t Number t Number<br />
%<br />
'<br />
•<br />
1954/55 969<br />
1955/56 644<br />
1956/57 . 1 072<br />
1957158 761<br />
1958/59 1 107<br />
1959/60 • . . 744<br />
1960/61 1 241<br />
1961/62 • .1 410<br />
1962/63 1 061<br />
•<br />
188 900 ,<br />
288 400<br />
174 300<br />
276 500<br />
361 100<br />
285 000<br />
195<br />
140<br />
375<br />
241<br />
267<br />
169<br />
282<br />
339<br />
130<br />
44 500<br />
26 200.<br />
93 200<br />
49 700<br />
62 600<br />
36 900<br />
55 400<br />
86 000<br />
32 400<br />
191<br />
240<br />
225<br />
289<br />
170<br />
(391)<br />
•<br />
40 000<br />
58 000<br />
" 63 000<br />
80 000<br />
48 000<br />
110 000 '<br />
328<br />
217 .<br />
508<br />
185<br />
257 •<br />
182<br />
321<br />
267<br />
(180)<br />
82 000<br />
40 100<br />
108 400<br />
35 700<br />
54 800<br />
31 000<br />
75 800<br />
(60 000)<br />
(43 000)<br />
•<br />
1 378 314 300<br />
1 871 463 800<br />
1.320 305 200<br />
2 133 ' 487 700<br />
2 186 555 100<br />
1 762 . 470 400<br />
57/58-62/63 1 054 . 262 367 238 53 833 251 66 500 232 50 050 1 775 432 750<br />
59,4 60,6 1;3,4 12,4 14,1 15,4 13,1 11,6 100,0 100,0<br />
1 In these figures are included the yields of sea trout that amount to 35 to 85 per cent in<br />
Poland. The Swedish yields have been re-calculated after the statements by Alm (1928a, 1954a)<br />
and Segren. Figures in parantheses have beén estimated.<br />
111'<br />
•
•<br />
the period from 1940 to '1962.<br />
- 54 -<br />
The figures for the landings for the total salmon and sea trout<br />
fishery show considerable fluctuations for the Baltic Sea and also for the<br />
rivers (Tables III and Iv). For the Baltic Sea they rose from 250 t to<br />
1330 t during the 20 years from 1913 to 1932. The most astonishing phen-<br />
omenon is, however, the sudden growth of the fishery after the Second World<br />
War to a total of 4000 t, which finds expression also in the rivers (700 t).<br />
The average yield for the years 1957 to 1962 amounted to 2675- t.<br />
Of this about 275 t were caught in the rivers. The shore.fishery (Sweden,<br />
Finland, SSSR, Poland) yielded about 600 t and the pelagic fishery 1800 t<br />
or 440,000 fish. This corresponds to a percentage of 67 per cent of the<br />
total yield. 'These catches were composed of 1500 to 1600 t Atlantic salmon<br />
and 200 to 300 t sea trout.<br />
Lp. 2581<br />
. The pelagic fishery (Denmark, Germany, Poland,Sweden) is res-<br />
tricted substantially to the main basin of the Baltic Sea (fishing grounds<br />
3, 4, 5, 6), but it has been extended recently during the fall months into<br />
the Gulf of Bothnia (fishing ground 2, Fig. 6).<br />
Since the fishing in the ocean is carried out preponderantly<br />
from fall to sprink, the seasonal yields are of special interest (Table 16).<br />
They show still greater fluctuations than the figures that relate to the<br />
calendar year. This is caused by the fact that the seasonal yields are<br />
affected especially by the fluctuations in the stock. At the beginning of<br />
the fishing season the salmon, which spend their second year in the Baltic<br />
Sea, are just entering the exploited phase..They form, together with the<br />
fish that are one year older, the main bulk of the catches. Towards the •<br />
.end of the seaèon, in April/May of the following year, the large fish<br />
'begin their spanning migration. This is the beginning of the rejuvenation •
Table 17. Monthly average weights of salmon, according to German landings, in kg,<br />
gutted weight.<br />
Season IX X XI XII . I II III IV V VI Weighted Arithm.<br />
- mean mean<br />
1954/55,<br />
1956/57<br />
1957/58<br />
1958/59<br />
1959/60<br />
1960/61<br />
1961/62<br />
1962/63<br />
1963/64<br />
3,92 .4,25 4,67 4,68 4,75 . 4,63 4,33 4,38 4,47<br />
4,87 5,79 5,88 6,68 - 5,21 5,31 5,10 4,52 5,36 5,42<br />
4,34 4,49 4,18 3,34 4,04 4,20 4,22 ' 4,02 3,70 4,02 4,06<br />
5,29 4,63 5,03 4,32 5,07 5,28 5,10 5,11 4,92 4,98<br />
3,98 4,32 4,13 4,31 4,44 4,67 3,94 3,72 - 4,27 4,18<br />
5,37 4,64 4,46 5,42 4,86 4,34 4,71 4,12 3,53 4,39 4,61<br />
3,29 4,95 5,18 5,09 4,98 5,31 5,35 5,09 4,42 5,10 4,85.<br />
3,55 4,05 4,13 3,90 3,62 3,85 4,14 3,87 3,89 3,84 3,91 3,88<br />
4,39 4,63 3,63 4,05 4,04 3,57 3,35 3,87 3,95<br />
4,93 4,38" z :..4,06 4,46 5,89 3,79 3,24 4,47 3,25 3,23 4,35 4,17<br />
Mitrelwert = mean val .4,04 4,72 4,35 4,55 4,69 4,73 4,55 4,61 . 4,18 3,70 4,47 4,49<br />
fiinfgliedriges Five-term<br />
' Mittel (4,37) 4,47 4,61 4,57 4,63 4,55 4,35 (4,16)<br />
Table 18. The monthly yields of the fishery in the main basin of the Ba3.tio Sea.<br />
SeasOn Country :VIII IX X XI XII II III IV V VI VII Total<br />
_<br />
Mitte1=Mean M. 1 1,2<br />
1955/56 bis =t0Dell 2<br />
1961/62 Po 3<br />
Svi 9,7<br />
4 • '<br />
23,3 92,8 162,8 219,6 144,0 90,4 85,5 80,1 77,5 23,4 * 0,5 1001,0<br />
1,0 11,7 52,9 63,3 39,9 24,7 31,5 19,1 11,7 1,3 • 259,1<br />
0,2 8,6 18,1 13,0 • 1,9 4,6 26,6 • 17,6 1,4 92,0<br />
35,7 30,6 31,8 11,3 3,4 2,8 17,2 28,2 21,8 5,2 0,9 198,5<br />
Ges. Mittel Tot .Mean '10,9 : 5 9,9 135,3 /56,0 314,3 200,3 - 11 9,7 138,7 153,9 1/3,6 ' 31,7 1,3 1550;6<br />
_. .<br />
I Schweden nur Gotland und Bleitinge: = Sweden. -only Gotland and Blekingè - ' .<br />
1 = Denmark 2 - Germany<br />
3 = Poland 4 = Sweden<br />
•
- 56 -<br />
of the stock. In the course of the summer a new crop of smolt (fish, which<br />
emigrated from the rivers in the same year) joins the exploited stock (see<br />
5.3.1.2.). This process is not reflected in the records of yield according<br />
to calendar years, because two different stocks are sampled at the beginning<br />
and at the end of the year. -<br />
The monthly trend of the average weight points also to the<br />
changes in the.exploited stock (Table 17). The figures increase from Sep- .<br />
constant until March and begin - to decrease<br />
in April. The incXease at the beginning of.the season is a consequence of .<br />
s the growth, although here other causes may play a role. The decline of the<br />
values that begins in April points'to the emigration Of the large salmon.<br />
In some years there occur deviations from these average events.<br />
The Danish share in the pelagic fishery in the Baltic Sea amounts .<br />
to more than 60 per cent, whereas the other countries have each an 11-per •<br />
cent to 14-per cent share in the landings. The largest landings of more<br />
than 2000 t or more than 500,000 salmon were reached in 195 6/7, 1960/1,-<br />
and 1961/2. The emallest yields occurred in 1957/8,and 1959/60 with. about<br />
1350 t or 300,000 salmon.<br />
The yeiarly trend of the landings (Table 18) shows that‘the<br />
.fishery reaches a peak at different times in the individual countries.<br />
Denmark and Germany have the highest yields in the winter months from Nov-<br />
ember to January. On acCount of inclement weather, the landings in Februare<br />
are often gmaller. This was especially pronounced during the 1962/3 season<br />
in the German fishery, becauselthe cutters had to stay in harbour from<br />
January until March on account of the iCe cover. When the water begins to<br />
warm up, the yield begins tà diminish in March.<br />
The fishery takes . a very different course in SWeden and in Poland.<br />
tember to January, they remain
- 57 -<br />
In February and March hardly any vessels are fishing so that the figures<br />
for the yield show peaks about the end of the year and in spring. The<br />
Polish statistics shows the greatest landings from November to January<br />
and from April to May. This separation is still more pronounced for the<br />
Swedish fishermen from Blekinge and Gotland, who carry out a pure fall<br />
fishery and who obtain the highest yields from September to November and<br />
from March to May.<br />
2.3.5. The composition of the catch in the pelagic fishery<br />
As has already been said, the sea trout are not recorded sep-<br />
arately in the landing statistics. In order to ascertain their shaxe one<br />
has to have recourse to market investigations.<br />
• The results of the available analyses have been summarized in<br />
Table 19. There are no Swedish records for the Baltic Sea proper'. When<br />
one assumes that the percentage of the Swedish share in seà trout ià about as<br />
high as the Danish one, one obtains for the total catch in the Baltic Sea<br />
proper 10 per cent in 1958/9, 25 per cent for 1959/60 , 12 percent for<br />
[p.:259]<br />
1961/2, and 22 per cent for 1962/3 of sea trout. In the Polish catches the<br />
share amonted in the.last few years numerically to over 80 per cent. In<br />
the proper Baltic 'Sea alone it ameunted to 20 per cent in the season 1959/60 . •<br />
In any case it is astonishing that up to one quarter of the yield of the<br />
pelagic salmon fishery consists in some years of sea trout.<br />
The'German Catches show'from January/February on an increase<br />
in the share of sea trout,loecause at that time the fishermen work frequ<br />
ently in the Danzig Deep. There the sea trout that originate'in the Vistula'<br />
occur in large numbers. The total catch. of a cutter at that time can occas-<br />
ionally conaist tô 70 per cent of this kind. Accordin'e, to the data at hand,<br />
the share of' seà -trout is independent of whether driftlines . -or driftnets<br />
are being used.
Table 19. The share of sea trout in<br />
the salmonid catches in<br />
the Baltic Sea proper.<br />
Weightéd<br />
Season Denm. Germ. Pol. me an<br />
1956/57<br />
1957/58<br />
1958/59<br />
' 1959/60<br />
1960/61<br />
1961/62<br />
1962/63<br />
Weighted mean<br />
3,0<br />
6,2 42<br />
2,4 3,3 60 10,8<br />
6,9 15,5 87 26,5<br />
3,4 84<br />
5,9 , 3,9 79 12,8<br />
1,5 12,8 87 24,4<br />
1 valid for January only; Danishand<br />
Polish figures after Christensen<br />
and Chrzan.<br />
5 8<br />
The cod plays the main<br />
role as a genuine companion fish<br />
in the salmon fishery. It is being<br />
caught mainly with driftlines, very<br />
rarely in nets (Table 20). The<br />
fishermen are of the opinion that<br />
the occurrences of salmon and cod<br />
exclude each other and they cite<br />
as proof that during a large catch<br />
of cod only very few salmon are<br />
being caught. Concerning this it<br />
must be .said that a hook that has already been taken by a cod, can no<br />
longer catch a salmon. Since there exists a food competition between the<br />
two species of fish, it is possible that an effect of gear saturation may<br />
be reached. According to the number x of the cod already hooked, we have<br />
then a catch of salmon, not per 1000 hooks, but per 1000 x hooks. The<br />
catches of salmon can be influenced in this way by the presence of cod.<br />
Vice versa, the yield of cod can also be influenced by the salmon. There .<br />
will thus become eàablished an equilibrium between the two species. A<br />
shift will always occur when the population density of one species changes<br />
in relation to that of the other.<br />
[P. 260]<br />
Effects of this kind can find expression in the ratio between<br />
the salmon catches with lines and in nets (Table 9) because cod are hardly<br />
cc..td.es<br />
ever caught in driftnets. The falsification of the ceptueeQ per unit effort<br />
of salmon can amount to a maximum cif . about± 0.5 salmon per 1000 hooks.<br />
This possible error, however, has to be neglected, because the necessary<br />
figures for a correction are not available,for all years.
• Table<br />
20. Additional catch of cod in the salmon fishery,<br />
yields and captures per unit effort.<br />
Number Month 1957/8 1958/9 59/60 60/1 61/2 6 2/3<br />
of cod<br />
• Sept. 2,3<br />
Okt. 10,2 19,7 15,0 6,2 0, 1 . 16,7<br />
per Nov. 44,7 24,9 27,7 23,0 7,6 9,5<br />
1000 pez. 21,0 14,7 DA 17,7 10,3 5,3<br />
Jan. • 26,5 11,7 8,5 UA 6,0<br />
hooks Febn 7,4 10,4 5,9 3,3 1,7<br />
Mâm 2,6 3,0 IA 1,4<br />
per 100 nets Apr./May 1,0 0,5 0,3 0,6 0,5 0,1<br />
Total number<br />
of cod . 100 000 45 000 48 000 34 000 30 000 12 000<br />
..... . .<br />
- 59 -<br />
Ceeke ,",<br />
Table 20 shows that the c-aptux-e.s per unit effort of cod and the<br />
yields have declined considerably in recent years. The decline of the<br />
catches has been caused, apart from changes in the stock of cod, also by<br />
. the reduction in the intensity of line fishery. The greatest yields of<br />
cod are Obtained in the months of November/December. Later the fish return<br />
to the sea bottom in order to form pre-spawning aggregations . and to move<br />
to the spawning grounds .<br />
The other species of additional catches are quantitatively of<br />
small importance, but they are worth noting on account of the species com-<br />
position. In the line fishery up to 20 sea hares (Cvolonterus lumpus) of<br />
a length of 10 to 15 cm axe caught during a voyage. Besides these there<br />
are found occasionally trigger fish and flatfish (flounder, turbot) and, •<br />
more rarely, mackerele In one case it is known with certainty that a<br />
seal has been caught on a hook. Guillemots that dive for the bait and<br />
gulls that feed on the intestines of hooked cod, are Caught frequently<br />
on the hooks by the bill. However, they can usuallY be freed and released.<br />
In drifnet fishing the flounder'plays the main -role as an
- 6o-<br />
additional catch. However, hardly more than 20 fish will be caught during<br />
one voyage. The plaice is represented in still smaller numbers. In spite<br />
of the large mesh opening, an occasional herring or small sea hare may be<br />
caught.<br />
Dolphins (especially Phocaena phocaena = harbour porpoise, and<br />
Delphinus delphus = common dolphin) are captured in every year, whereas .<br />
the grey seal is caught more rarely. I have records for the season 1959/60<br />
of the capture of a dolphin and a seal, and for the season 1961/2 of three<br />
dolphins and ohe seal.. Ducks become entangled regularly in the driftnets.<br />
3 •<br />
The sexual maturation of the<br />
Baltic Sea salmon in the ocean<br />
The propagation in salmon takes place generally in such a manner<br />
that the maturing males and females migrate from the sea into their home<br />
streams where they spawn in late fall. In the spring the frY emerges from<br />
the eggs that lie in the gravel at a depth of about 20 cm. After one to<br />
five years the young transform into smolt and migrate in the spring into .<br />
the sea. They grow up and in their turn seek but their home streams for<br />
spawning. The so-called grilse, which are mainly males, spawn already after<br />
the second summer in the sea.<br />
.<br />
Exceptions from this rule have been established early. C.<br />
Gessner (1558) knew already that small males take part in the spawning act<br />
without having visited the sea previously. This fact has been described<br />
anew in 1906 by Calderwood (according to K. A.Pyefinch 1955) and G. Alm<br />
(1943) tested it experimentally and confirmed it.<br />
It has been known for a long time that the species of Oncorhvnchus .<br />
and the Atlantic salmon have formed landlocked stocks (accOrding to E.<br />
'NereSheimer 1941). Such forms exist in Japanese lakes, in North American
•<br />
100<br />
50<br />
60<br />
100 cm<br />
Totallarle<br />
.<br />
20<br />
d = '9 = ----, n ------ 997<br />
= Total length.<br />
Fig'. 12 .. Distribution of lengths and--gonati--1-ength-s—ef<br />
crç Sal- e-ko<br />
eke 1.3..êtqc, .seixtryaed., b<br />
- 61 -<br />
fresh-water bodies (Labrador, Maine), in Lake Ladoga and Lake Vânern.<br />
Dahl (1914-26) found them arso in the lakes of the river Otra. These<br />
[p . 261]<br />
salmon live in land-locked waters that were formerly connected with the<br />
sea. Their entire life is therefore spent in fresh water. Females and males<br />
become mature there and migrate'into the rivers to spawn.<br />
This knowledge showed that salmon do not absolutely require<br />
the change of environment from fresh water to the sea and back. It came,<br />
however, still as a Surprise when Danish fishermen succeeded in about 1925<br />
in raising females from artificially fertilized eggs. These females matured<br />
after four years in the fresh-water ponds and spawned three times in suc-<br />
cession (V. O. Otterstr8m 1933). To be sure, the fish attained a length<br />
Of only 42 cm after five years.<br />
Anzahl Lackse = 'Number of salmon<br />
.Recently . Swedish scientists succeeded in . repeating the ex-<br />
periment and they have furthermore raised Atlantic salmon already to the<br />
fourth generation in fresh water (pers. communication from B. Carlin).<br />
However, the other extreme is also possible up to a certain<br />
'degree. I know of four cases in which female saimon-of 1959 to 1964 with
•<br />
- 62 -<br />
discharging gonads were caught during the months November to February in<br />
the Daltic Sea. Mature males are also found occasionally. Nordgaard (ac-<br />
cording to Nereheimer 1941) also has demonstrated that salmon can mature<br />
in the sea. Fertilization and development of the eggs, however, is not pos-<br />
sible, because all the necessary conditions for this are lacking in the<br />
ocean.<br />
The development of the gonads in the rising mature salmon, the<br />
act of spamning, the Conditions for fertilization and the embryonal dev-<br />
elopment have in pari investigated very thoroughly. There are, however, no state-<br />
menté about the sexual circumstances during the maritime stage.<br />
3.1. The sexhal composition of the exploited stock<br />
If we assume.that the newly hatched brood consists of equal<br />
numbers of males and females, then among the migrating smolt, the females<br />
must be in the majority, because some males always remain in the rivers.<br />
During the 'second year in the sea, the numerical proportion among the -sexes<br />
LP.26 2] •<br />
continues to shift in favour of the females, because already more males<br />
(eilse) than females have migrated to the spawning grounds. The investig-<br />
ation of the salmon catches at sea should therefore yield more females than<br />
males.<br />
In this connection we shall examine the composition in regard<br />
to length and sex of eight salmon catches of 997 fish from the-years 195 8 .<br />
and 1959 (Fig. 12). The sexual figure 6 amounted collectiveiy to 0.391.<br />
Thé value for the fishing ground 6 (Bornholm) was 0.438, that for the .<br />
fishing ground 5 in contrast only . 0.371. The differenoes between the two<br />
fishing grounds are, however, notiignificant, since the value 0.438 is<br />
••■■■■•■•■••■■••••■•■•■■■••••••■•■••••■••■••••■••■••■■■•••••••<br />
6 After A. BUckmann (1929). The decimal fraction that indigates the proportion<br />
of males is called the Sexual figure.
• subject<br />
to an error of ± o.op95.<br />
1<br />
30<br />
s.20<br />
10<br />
CM<br />
Gonadenlânge Length of gonads<br />
50<br />
6..4%<br />
• • .<br />
70<br />
, . • '<br />
. '<br />
• • • •<br />
• • •<br />
• o•<br />
• • • •<br />
.90<br />
6 3<br />
110 cm Totallânge<br />
Fig. 13. Relation between total length and gonad length of<br />
the long gonad in the salmon, Nov./Dec. 1959.<br />
Total length<br />
In Fig. 12 the distribution of the lengths of both sexes shows .<br />
two maxima that correspond substantially to sea year clasSes 7 A.1+ and A.2+..<br />
•■•■•••••••••••••■••••••••••••••••<br />
7 - in the second winter in the seà, A.2+ = in third winter in the sea.
- 64 -<br />
It is found that the sexual figure for both sea year classes is very<br />
different. It amounts to 0.446 ± 0.0195 in group A.1+ and to 0.260 ± 0.255<br />
in group A.2+. This difference points to the fact that during the third<br />
year in the sea at least as many males have migrated as females. The sexual<br />
ratio can therefore not be considered as constant. Since the strength of<br />
the year classes and with it the ratio between the two sea year classes<br />
A.1+ and A.2+ changes annually, the sexual composition of the exploited<br />
stock must also undergo this change. It is thus not the numerical ratio [ p. 263]<br />
of the sexes in the total catch that deserves our special attention but<br />
that in.the two age groups.<br />
Since the sea year class A.2+ in the sea comprises 74 per cent<br />
females) these must also predominate on the spawning ground. As has already<br />
[19 . 264]<br />
been explained, the missing males of this age class can be replaced by the<br />
numerous emigrating younger males. This, however, does not provide the<br />
solution for the problem of the sexual ratio on the spawning ground. When,<br />
for example, two very weak year classes follow on an exceptionally strong<br />
year class, then it must be taken into account that the younger males and<br />
grilse of the two weak year classes are not present in numbers sufficient<br />
for the females of the strong year class. Here nature has obviously taken<br />
precautions through the mature parr; because these fish were not subject<br />
to the strong depletion of the stock in the sea they are probably always<br />
present in sufficient numbers in the rivers.<br />
.<br />
3.2. The conditions of the gonads<br />
According to A. Backmann (1929) there are two conceptions com-<br />
bined in the word "maturation": the process of the development from the<br />
juvenile fish to the sexually mature one during its first period of life,'<br />
'Which happens, only once, and the obtaining of sexual maturity (sexmsa
cycle) during the second . period of life, whih is usually repeated period-<br />
ically.<br />
Fig.'14. Long gonad of a female of the sea year class A.2+.<br />
(a) full view, .(b) partial view, (c) gonadal discs.<br />
In the female the primitive germ cells give rise to the oogonia<br />
through mitotic divisions. The oogonia grow into oocytes of the first order.<br />
The meiosis that follows leads through oocytes of the second. order to the
Opcytenzet<br />
Numbep<br />
20<br />
I0<br />
- 66 -<br />
formation of mature ova. The strong growth of the female sexual products<br />
through increase in the amount of cell content and through yolk deposition<br />
and water uptake takes place after the diplonema stage of chromosome cor›-<br />
jugation and before meiosis. Since this process can also be observed during .<br />
the periodic - attainment of -spawning maturation in the second period of<br />
life, it can be assumed that in the sexual cycle of adult fish maturation<br />
begins with the enlargement of the oocytes.<br />
.<br />
The stock of salmon in the Baltic Sea is composed almost exclus-<br />
ively of such fish that are in the first period of life and have nôt yet<br />
spawned. The fish of the age class A.1+ have atill almost one or two years<br />
of sojourn in the sea ahead of them and must be designated as juveniles<br />
in the customary sense.<br />
In the following it will be - examined whether the ovaries undergo<br />
a change in the sea, and whether it is posàble to ascertain the probable<br />
time of spawning already at this stage.<br />
3.2.1. The ovary<br />
of oocytes ,<br />
, . . ,<br />
,<br />
, f<br />
1<br />
■<br />
, ..• .<br />
I ■ .<br />
I<br />
.. •<br />
—■<br />
ttesch.u. Cen %re diees<br />
End discs .<br />
,<br />
Fig. 15. Size of egg in different regions of the ovary<br />
. (means of 12 salmon, 74 to 79 cm total length).<br />
• The ovary conditions were investigated in 68 females that were<br />
) .<br />
from 43 to 104 cm long. Three fish were in the first year of their star<br />
in the Baltic Sea, 31 fdsh were in their second year and 34 fish were in<br />
».11<br />
20 mm<br />
Egg- diameter<br />
•<br />
Enturchmesser
•<br />
their third year.<br />
, Recruitment oocytes<br />
-<br />
'maturing eggs<br />
Fig. 16. Cross-section through a salmon ovary,<br />
age class A.2+ (X 20).<br />
EMurchmesser = egg diameter<br />
mr. Number Of maturing<br />
oocytes<br />
Anzahl redender Oocy ten<br />
o mittlerer Oocytendurclynesser<br />
Mean diameter of<br />
• oocytes<br />
w 10 30 0<br />
IllAnyohl rellender<br />
Oocyten<br />
Number of<br />
aturing<br />
oocytes<br />
„ .. . . . . Ovary discs<br />
Fig. 17. Mean diameter of occytes and number of oocytes<br />
in different ovary regions.<br />
200<br />
Ovorscheiben<br />
- 67 -
Anzaht number<br />
5 Ttere,74-79cm(0 75,6cm)<br />
April 1958<br />
6 Tier. 74-79cm (0 77,1cm)<br />
Tiere = sh<br />
2 Tiere, 77- 79cm (.0 78,0c ini<br />
3 lier,99-101cm (0100,3cm)<br />
2 here,100-101 c m( 10Q cm)<br />
5 7n.re, 91-99 cm<br />
. 96,6cm)<br />
3 Per., 97-99cm<br />
(099,3cm)<br />
Fig. 18. - Abundance distribution of salmon oocytes of<br />
different diameters.<br />
- 68-<br />
The diagram of the relations between length of gonad and body<br />
length (Fig. 13) shows that the ovaries of the salmon in the Baltic Sea<br />
have lengths of from 5 to 31 cm, generally from 8 to 18 cm. Correlation<br />
with 'body length'is obvious, however, the values show strong scatter.<br />
Fig. 14 shows the long gonad of a female of the sea year class A.2+. It<br />
[1).<br />
can be seen plainly how the connective tissue surrounds the dorsal‘side<br />
of the ovary. From it are loosely suspended the discs that are formed<br />
[P. 266 ]<br />
267]
50<br />
r-■ 2<br />
/ bet; 56cm = 1 fis<br />
1 lief; 76cm<br />
7s ere , 68-78cm (073,0cm)<br />
1 net; 73cm<br />
2 T ere, 86-88cm (08Z0cm<br />
2 Tiere,43-48cm (~ 5 5 cm) = 2 f ish<br />
Fig.<br />
9 Tiere, 54-72cm (063,8em<br />
5 Tiere,89- 96 c m(08Z .4cm)<br />
3 I ■ere,8t -98cm (091,3cm)<br />
Apri11960<br />
6 Tiere,92 -102cm (093,0,cm)<br />
November 1959<br />
2 bere,82-86cm(84,0cm)<br />
bere,90- 94cm<br />
9Z0cm)<br />
Oocyferedurchm<br />
2 3 mm<br />
diameter of oocytes<br />
18. (continuation).<br />
irregularly and separated from one another. The ripe eggs are later<br />
loosened from the follicles in the disc's and fall into the body cavity.<br />
Cutter t)r-1<br />
Each ovary has orall a blunt end and the circumference is greatest there.<br />
Caudally the gonad is'drawn out into a long point.<br />
The number of discs in the longer ovary is 41 to 59, with a<br />
mean of 47.7; in the shorter ovary the number is 31 to 52, with a mean<br />
of 43.1. On an average the number of discs in the shorter ovary is 9.6<br />
per cent smaller than in the longer-one. This difference is, however; not
- 70 -<br />
expressed to the saine degree in the number of eggs. Since the shorter<br />
gonad is generally slightly thicker than the longer one, it has on an av-<br />
erage only 8.6 per cent fewer eggs than the longer ovary.<br />
3.2.2. The maturing of the oocytes<br />
According to C. F. Hickling and E. Rutenberg (1936), R. Undler<br />
and W. Pirwitz (1957) and others, the ovary of every fish contains a gene-<br />
eral stock of small oocytes. A part of this stock matures annually. To re-<br />
place it, neW oocytes develop in the envelope of connective tissue. The<br />
development until maturity takes at least two years.<br />
We had 72 salmon ovaries for investigation at our disposal. Of<br />
these, 30 were preserved in formaldehyde at sea in April 195 8 , 22 were<br />
*preserved in November 1959, 20 in November 1959, and 20 in April 1960 at<br />
[p.268 ]<br />
sea in Gilson's solution. The oocytes of 68 ovaries were later removed from<br />
the follicles and measured individually under a stereoscopic microscope<br />
with the aid of an eyepiece micrometer' at magnifications of 12.5 or 32. ›<br />
In 40 ovaries all maturing oocytes could be counted..<br />
These investigations showed that the two groups of sizes cited<br />
above occur in the female gonad (Fig. 15). The small oocytes have a dia-<br />
meter of less than 0.3 mm. In the large oocytes the diameter varies be-<br />
?<br />
çy **" tween 0.3 and 3.4 mm. In Salvelinus fontinalis, V. slk, Vlad/kov (1956)<br />
designated the smaller oocytes as recruitment stock and the larger oocytes.<br />
as maturing eggs. In what follos these designations will be used also for<br />
the two groups of sizes of oocytes in the . salmon that have been cited<br />
above.<br />
oocytes<br />
A cross-section through the ovary }lows that recruitment stock<br />
occurs scattered through the entire ovary (Fig. 16). It is, however,<br />
especially freqUent in the connective tissue of the dorsal side of the
•<br />
- 71 -<br />
ovary that has already been mentioned (Fig. 14). The follicle-forming<br />
tufts of this tissue extend deeply into the gonad. Whereas the maturing<br />
oocytes separate easily after treatment with Gilson's solution, the re-<br />
cruitment stock sticks very tightly in the tissue and is often invisible<br />
and thus not amenable to quantitative treatment. Maturing oocytes are sup-<br />
plied plentifully with yolk, whereas.the recruitment stock haà no, or hardly<br />
any yolk. The oocytes of the recruitment stock are, however, of different .<br />
sizes (Fig. 15). The number and the diameter of the oocytes vary greatly<br />
in the different regions of the ovary on account of the varying size of<br />
the discs (Fig. 17). In the discs that are situated in the region of the<br />
greatest circumference of the"gonad, the diameter of the oocytes and their<br />
huMberece greater than in the end discs. The number of maturing oocytes<br />
in 12 . salmon with a total length of between 74 and 79 cm varied from 49<br />
to 205 per disc. The weighted mean was-134.<br />
• It will now be our task to investigate the development of the<br />
oocytes in salmon of different length and of different age and to find an<br />
indication of the probable time of spawning. Hitherto it has been known .<br />
through investigations of the stock that in the spring of every year a<br />
part of the salmori in the sea of sea year class A.2 8 and the majority of<br />
the sea year class A.3 8 emigrate to spawn. Thus one has to take into ac-<br />
count that at least some of these fish have reached a stage in their dev-<br />
elOpment in April that enables theM to spawn in the following fall.<br />
. The synopsis of the results shows that even in such salmon<br />
that have been caught at the saine time there are considerable differences<br />
in the diameter of the oocytes. It was not immediately possible to make .<br />
an unambiguous distinction between salmon with Well-developed gonads,<br />
8 A.2 = two years in the Baltic Sea, A.3 = 3 years in the Baltic Sea (cf. 5.1.).
- 72 -<br />
which could be expected to participate in the next spawning, and those<br />
Whith slightly developed ovaries, who would migrate to spawn only a year<br />
later. To begin with, those fish who showed an approximately 'equal dis-<br />
h). 269]<br />
tribution offrequency of diameters of maturing oocytes were combined (Fig.<br />
18). Thus a certain grouping was found in the salmon that had been caught<br />
in November 1959. The females of the age class A.1+ (57 to 77 cm fork length)<br />
had'a mean diameter of the oocytes of below 0.9 mm. In the females of the<br />
age class A.2+ (82 to 97 cm forklength) it was more than 1,2 mm.<br />
There is a possibility to test whether the indicated grouping<br />
is correct. In this case it represents two developmental stages. The fish<br />
who will participate in spawning in thé following year are distinguished<br />
from those who will spend another year in the Baltic Sea by having gonads<br />
that are better developed. It can, however, be expected that the grouping<br />
mentioned will be much better expressed in April 1960 - that is, at about •<br />
the beginning or shortly before the spawning migration. In order to pursue<br />
this idea, the mean diameter of the maturing oocytes has been ascertained.<br />
Accordingly, the frequency diagram of the mean diameter of the oocytes<br />
shows for each catch sample two,maxima (Fig. 19), that correspondto the<br />
groups cited. The samples of November 1959 and of April 1960 are most'suit-<br />
able for our consideration, because in this case the same year classes<br />
have been considered. Furthermore, they concerned only ovaries that had<br />
been prepared in Gilson's solution. In November the mean diameter of the<br />
oocyteads 0.59 and 1.44 mm, respectively, for both groups. The fish.that<br />
are represented by these maxima must appear also in the sample of April<br />
1960. In Fig. 19 We can recognize them again by the,two maxima in the<br />
frequency distribution. They show mean diameters of the oocytes of 0.96 '<br />
• and 1.99 mm, reSpectiVely. During the five months from November. 1959 to
5<br />
- 73 -<br />
April 1960 the diameter of the small oocytes increased on an average by<br />
0.37 mm, that of the large ones by 0.55 mm.<br />
It has still to be clarified which of the salmon represented<br />
in the samples will emigrate next in order to spawn. We can assume that<br />
the fish that had large oocytes. (over 1.2 mm in diameter) in April 1960<br />
would have soon started to emigrate and would have spawned in the fall of<br />
1960. If such fish were not to migrate in the normal manner, we should<br />
then find salmon with still larger oocytes in the Baltic Sea in November.<br />
That was, however, not the case. It is more difficult to resolve the ques-<br />
tion how those fish will behave whose ovaries contain only smaller oocytes<br />
(under 1.2 mm diameter). The large oocytes have to increase between April<br />
'Antel= Number of salmon<br />
Lachse<br />
À<br />
M<br />
•<br />
À•<br />
•<br />
April 1.960 •<br />
ra; 4701 Affiwe' •Act<br />
lor<br />
.ÀUWÀ<br />
l■ioverilber1959<br />
April 1958<br />
3 mm<br />
thiftlerer0ocytexiurchmesser<br />
Mean diameter of oocytes<br />
Fig 19Thefreqiency distribution of the mean diameters "<br />
of maturing oocytet)<br />
and November, the main spawning month, from 2.0 mm to about 6.5 mm (by about<br />
4.5 mm). From this point of view it would be possible that'also the smaller<br />
[P. 270 ]<br />
maturing. oocytes could grow from 1.0 mm to 6.5 mm (by 5.5 mm) on an aver-<br />
age. If that is possible, it would be hard to understand, why there are<br />
two groups of salmon with clearly different sizes of ovaries, and why then<br />
[p. 271]<br />
most salkon with smaller oocytes do not also emigrate to spawn. This latter
- 74 -<br />
is, however, not the case, because in November fish with greater oocytes<br />
are present. These can only have grown up from the small oocytes.df April,<br />
in that their diameter increased frOm 0.96 to about 1.44/ that is by about<br />
0.5 mm on an average.<br />
In order to make still clearer the reported train of ideas, the<br />
diameter of the oocytes will now be considered in relation to the length<br />
of the salmon. The evaluation of the sample of November 1959 ( Fig. 20 h)<br />
3<br />
llocytendurdwness e; mill<br />
r Diameter of oocytes<br />
10 30<br />
. _ .<br />
.<br />
•• .<br />
Total length<br />
50 70 93 rotadnytc il rn .<br />
Fig. 20 a. Relation between total length and diameter of the maturing<br />
oocytes, April 1958, length distribution of the age classes: A.?, 65<br />
to 86 cm, max. 72 to 79 cm; A.3, 87 to 101 cm, max. 90 to 98 cm.<br />
shows that it is pOssible to distinguish between recruitment stock and<br />
maturing oocytes in salmon already during the firstyear in the Baltic Sae&<br />
Up to a length of 76 cm the Size of the oocytes correlates with the length<br />
of the fish. That, however, does not hold for the samples of April 1958<br />
and April : 1960.(Figs. 20 a, c). Furthermore, it does not hold true for the<br />
larger fish (A.2+) of all three samples.<br />
ACcording to the findings, the process (fàf maturing during the<br />
sojourn in the Baltic Sea can be explained in the following manner:<br />
during the first year in the Baltic Sea recruitment stock and maturing .
- 75 -<br />
oocytes can be demonstrated in the ovaries of salmon (Fig. 20 b, fish 43 to<br />
54 cm long). (It is possible that the differentiation into these categories<br />
had taken place already earlier.) Whereas the size of the recruitment oocytes<br />
changes little during the subsequent time, the maturing oocytes show an<br />
3<br />
2<br />
Oocytendurchmesser Diameter of oocytes<br />
mm<br />
Fork length<br />
10 30 50 70 90<br />
Crobelleg4grm<br />
Fig. 20 b. Relation between fork length and diameter of maturing oocytes,<br />
Nov. 1959,. length distribution of the sea year classes: "A.1+, 57 to 77<br />
cm, A.24., 82 to 97 cm, A.+, 43 to 54 cm.<br />
almost linear increase" in their diameter that is correlated with the length<br />
of the fish (Fig. 20 h) until the second winter of their life in the Baltic<br />
Sea. During the progress of the growth of the oocytes this correlation does<br />
[p. 2721<br />
no longer exist later (Figs. 20 a, c). Salmon who have a diameter of the<br />
oocytes of more than 1.2 mm spawn already in the approaching fall4"that<br />
is, after a stay of 2.5 years in the sea. The other fish proPagate a year .<br />
later (Fig. 21). A Resell. (1893) gives a table of the egg maturation during<br />
the course of a year in his_investigation of the salmon in the Elbe. The<br />
values given for the months February to November fit excellently the curve<br />
for the age class A.3 in Fig. 21. Fritsch, however, did not state the age<br />
of his fish.<br />
It becomes clear in general from the data for April (Figs. 20
- 76 -<br />
a, c) that the age of the fish plays a.certain role in the growth of the<br />
oocytes. Within an age class, however, the process - of ripening is depen-<br />
dent on the length. At any rate, Fig. 20 a shows oocytes in both age classes<br />
for which it is not possible to decide with certainty whether they will<br />
mature already in the current year.<br />
3<br />
.2<br />
Oocytundurchtnessecrnal D inmeter of odcytes<br />
Fork length<br />
ZO • 60 80 .100<br />
GabellÉinge, cm '<br />
...____. . _... ._ - _. ... .<br />
Fig. 20 c. Relation between fork length and diameter of oocytes in April<br />
1960, length distribution of the age classes: A.2, 63 to 80 cm, max. 66<br />
to 75 om,A.3, 84 to 101 cm, max. 88 to 96 cm.<br />
If we attempt to group the salmon according to their degree of<br />
maturity with the aid of the diameter of the oocytes, we find for the fish'<br />
investigated:<br />
Sea year class A.+ A.1+ A.2+<br />
Nmber of salmon investigated 3 32 33<br />
of these in preparation for spawning in the follwing fall - 1 32
. ineftlerer Mean<br />
OocytendurcArnesser<br />
6<br />
F;u0<br />
diameter of oocytes<br />
Range of rariatiOfl of<br />
Vanotionsbrede ors<br />
/run! 00cyte6durchm. diameter of<br />
aturing ooc<br />
the men<br />
the oopytes<br />
. tes<br />
■ ocytes;<br />
xx relit/nit Oecyten<br />
00 Nachwuctisoocyten ecruitment<br />
x4 inechAFrifscM9.0 e<br />
----Rehmg.wftw ,M,i'verrem'ie4XT;'<br />
-,--wahrsch - • - -<br />
1 11.1 r<br />
0-<br />
W d V vi Vil? X XII a<br />
LO<br />
AO Ai<br />
///'<br />
r<br />
é1 eld X k.<br />
A'<br />
Sea yekr classes<br />
1.<br />
1<br />
1<br />
elorare—*<br />
A 3Heerjohreskossen<br />
• Fig. 21. Maturing of the oocytes in the Baltic Sea salmon..<br />
- course of maturing when attaining maturity after 3 1/2 years<br />
in the sea<br />
• course of maturing when attaining maturity . after 2 1/2 years<br />
. in the sea]<br />
3.2.3. Comparative discussion of the findings about sexual maturation<br />
The material on whieh is based the investigation of the matur-<br />
ation of the eggs is not very large. At any rate, the results point to<br />
the fact that is well-known from the investigations of the stock, that<br />
[P. 273]<br />
some salmon of the sea year class A.2 and the majority of the individuals<br />
of the class A.3 emigrate in the epring ofeach year in order to spawn.<br />
According to the investigations of the fat metabolism the<br />
amount of Let content P lays an important role.in the readiness for the<br />
sPawning migration. L. Scheuring (1929) is of the opinion.that the tiMe<br />
of- emigration from the sea depends not so much on the state of development<br />
of the gonad.than on the general condition. F. R. Hayes (1949) was able
- 78 -<br />
to show in an investigation of the chemical conditions of the salmon eggs<br />
that fat is the most probable source of energy for the development of the<br />
embryo. In addition, fat is being deposited in the gut mesenteries of the<br />
yolksack-brood befors the first intake of food - .<br />
F. Thurow (19 62) was able to demonstrate that the storage of<br />
fat in the Baltic Sea salmon is correlated with the readiness to spawn.<br />
The salmon of the age class A.1+ show during late fall, with<br />
an average of 14 Per cent fat content, a value that is hardly lower than<br />
in fish of three winterS(A.2+). In the winter most of the younger fish<br />
suffer a considerable deterioration in condition, so that the fat content<br />
falls to an average of 6.5 per cent. The larger and older fish are able<br />
4.5s<br />
to keep the food supply so favourable that only a very slight consumption<br />
of fat takes place. Whereas the salmon of two winters lose more than 50<br />
per cent of the fillet fat, this loss in those of three winters amounts<br />
to only 10 per cent, so that their fat content in epring amounts to about<br />
12 per cent. According to this there are two developmental phases during<br />
the sojourn in the Baltic Sea. During the first phase, which ends in general<br />
in the late fall of the second yeaT in the sea, fat is predominantly being<br />
stored up to a content of 14 to 15 per cent. When the fish succeed to keep<br />
the loss in condition so low that the fat content does not sink below about<br />
12 per cent, then these salmon can take part in the spawning emigration<br />
in the spring. In the other case they remain in the Baltic Sea, attain<br />
again a content of 15 per cent fat until November and then survive the<br />
winter so well that they can emigrate to spawn after a three-year stay in<br />
the sea. When we compare these results with the findings of the investig<br />
ations of the oocytes, we find here also the expression of the two phases<br />
. that have been mentioned (Fig. 21)". The formation of the fat depositsi;that
- 79 -<br />
furnish the energy fer the spawning migration and the maturing of the oo-<br />
cyte e appear thus to proceed hand in hand.<br />
D. R. Idler and B. Bitners have determined the energy consump-<br />
tion of Oncorhynchus nerka during the migration from the river mouth to<br />
thé spawning ground. They did find that a female of 2.2 kg weight requires<br />
on an average 1.1 kcal/kg/km. The Baltic Sea salmon have to travel distances<br />
of 700 to 1300 km from the southern Baltic Sea to their spawning grounds.<br />
Although the travel in the Baltic Sea . certainly requires the expenditure<br />
of less energy than in the rivers, we shall take the value of Idler and<br />
Bitners as basis. Here it has to be taken into account that the salmon have<br />
fat deposits not on4r in the fillets, but also in the mesentheries of the<br />
intestines, which contain one-third to one-half as much fat as the fillet.<br />
A aalmon of about 70 cm length has a live weight of about 3 kg and therefore<br />
30û0<br />
requires about(3kcal for 1000 km. Since oils, liver oils and the like have<br />
a content Of about 900 kcal per 100 g substance (J. R. Geigy 1953), about<br />
350 g fat will be required for 3000 kcal. This amount corresponds to a fat<br />
content of about 12 per cent in the fillet (110 g intestinal fat, 220 g<br />
fillet fat; fillet weight = 60 per cent of the live weight). To overcome<br />
a migration distande - of 1000 km a fat content in the fillet of about 12<br />
per cent is required.<br />
The analysis of the age of the ascending salmon can undoubtedly<br />
show best at what age the salmon emiàrate from the Baltic Sea in order to<br />
spawn. To be sure, an unambiguous material should contain results from the<br />
P. 275]<br />
most important spawning rivers. For this I have three series of meaaure-<br />
ments that have kindly put at my disposal by B. Carlin. In one case these<br />
concern beach-dragnet catches of 715 salmon, which were caught between June<br />
12 and September'2, 1959 in the Ingermanâlven. The second series concerns
Anzon/I Number<br />
50<br />
SO<br />
100<br />
100<br />
100<br />
SO<br />
70<br />
90<br />
Kohx, 36 - 88 1962<br />
Karsinopoton 621 St<br />
Totallânge Total length<br />
Baltic Sea ProPer<br />
Eigenfl. Ostsee, nprtt 1962<br />
frelb"tz 691 Driftnet<br />
r° i'llange Total length<br />
Lule, A6.-318.1961<br />
Korsinopatan 1741 St<br />
Totalbringe<br />
Total - length<br />
Baltic Sea proper<br />
Eigentl. Ostsee, Jon. 196<br />
Trelbangel 1329 St. Driftline<br />
Gaboliaref Fork length<br />
4ngermanOlven,12.6.- 2e 1959<br />
Woe. (not) 715 St. Seine<br />
raft'llenge Total 'length<br />
Baltic Sea, proper<br />
Eigentl, Ostsfte, April 1959<br />
Treibnetz 575g!. Driftnet<br />
Gabeiliinge Fork length<br />
110 Cm Lange tength‘<br />
Fig. 22. <strong>Series</strong> of measurements for salmon,<br />
Baltic Sea and Swedish rivers<br />
(the Swedish measurements were kindly put at<br />
my disposal by B. Carlin).<br />
- 80 -<br />
[p. 2741
'<br />
1741 salmon, which were.caught betWéen June 4 and August 31, 1961 in the<br />
river Lule. A third series concerns the salmon that rose in June/aly in<br />
the river Kalix. There are no age determinations available for these<br />
catches. However, an estimate of the age' composition can be made when one<br />
*compares the samples with catchesl‘rom_the Baltic Sea proper. '<br />
Wé know from Swedish tagging experiments (B. Carlin 1959 a)<br />
that the majority of the Swedish spawning fish of the Swedish rivers has<br />
lived previously on the feeding grounds of the Baltic Sea proper. Driftnet<br />
catChes from the Baltic Sea itself in April 1959.consisted of 70 per cent<br />
salmon of the sea year class A.2; with lenehs.:of 64 to 82 cm (fork length)<br />
and about 30 .per cent predominantly of the sea year class A.3. (Fig. 22).<br />
•Thesé fish cannot have grown very much more until a possible immigration<br />
into the Anegermaneven in July/AAgust. We can therefore aesume that the<br />
length group in the séries of measurements from the Ingermanalven that<br />
has a maximum at a length of 72 to 82 cm consists also of fish of the same -<br />
sea year class, which has now to be designated as A.2+. These fish<br />
amounted tcabout 66 per cent of the total catch, thatis,'4 per cent less3'<br />
than in the catches from the Baltic . Sea proper. There is a similar/agreement<br />
in the series of Measurements for the year 1962 in the agé class A.2 with<br />
86 per cent (Baltic Sea) to 84 per cent (Kalix). In the year 1961 the con-<br />
ditions are lesa unamliguous. The catches from the Baltic Sea in January<br />
consisted to 77 per cent of salmon of the age class A.2. These fish had<br />
grown extremely well in comparison with other years so that.the length dis-<br />
tribution of the aàe classes A.2 and A.3 did overlap very widely. The coryroufs<br />
responding catches of spawning âwarms in the river Lule showed the same<br />
picture. Therefore it is not possible to separate the two age classes on<br />
• the basis of léAgth distribution. In addition there appeared in the river<br />
8 4f.
Laie a large number of'grilse, which are practically not being taken in<br />
the Baltic Sea.<br />
G. Alm investigated the age composition of spawning swarms in<br />
the rivers Torne, Kalix, Lule, Pite, Ume,. and M8rum. The number of the<br />
in each sample, it is true, was only 21 to 337. The age<br />
classes A.2 and older comprised 94 per cent of the total catches. Of these<br />
36 per cent belonged into the age class A.2.<br />
Thé series of meaelrements,from the Swedish rivers in the years<br />
.1959/62 indicate that the share of the age class A.2+ in the spawning<br />
stock is at present considerably greater than the percentage of salmon that<br />
have spent more than three years in the Baltic Sea. In supplementing these<br />
data we qan employ investigations about the share of salmon with spawning<br />
marks in catches from the Baltic Sea. These fish are those that had already<br />
spawned and had then ±eturned into the Baltic Sea. The energy required for<br />
the journey and the act of spawning is supplied by the body reserves. This<br />
includes a degradation of substance at the scale'margin. This absorption<br />
zone is called the spawning mark. 8Cale samples for age determination had<br />
been taken of à total of 6914 salimmthat had been caught in the sea. Among<br />
these were 166 fish•(2.4 Per cent) that had already sPawned. If we neglect<br />
the grilse and consider only the spawning times of 1957 to 1961 in which<br />
all spawning age classes were fully included, it is found that 63 per cent<br />
of the salmon with spawning marks had spawned in the third year of their<br />
sojourn in the sea and 37 per cent had spawned later (Table 37). In the<br />
preceding it has been attempted to employ the series of measurements in<br />
the rivers, the share of salmon with spawning marks, the conditions of'<br />
the salmôn and the maturing process of the ovaries as indicators for the •<br />
age at the time of spawning. Here we see at ance two different results:<br />
fish analysed
•<br />
- 83-<br />
the series of measurements and the analysis of scales showed that the share<br />
[p.276]<br />
of the sea year class A.2+ in the number of spawning salmon was greater .<br />
than the share . of all older fish. In contrast to this, the analyses of fat<br />
and the examinations of the maturity give the impression that a amaller<br />
percentage of the sea year class A.2+9 than the older fish does spawn.<br />
This apparent difference becomes explicable when one reflects that both<br />
results have a different relative basis. In the first case we start from<br />
the spawning' stock in the rivers, in the second case we start from the<br />
exploited stock in the Baltic Sea. Wé can establish a connection between<br />
the two figures only through the total number of the spawning fish that<br />
emigrate from the Baltic Sea. However, we do not know this figure.<br />
Table 21. The percentage of spawning salmon in<br />
the sea year classes A.2 and A.3 and older under<br />
the assumPtion of different shares of the<br />
migrating salmon in the total stock.<br />
Stock in the. Baltic Sea, 1958-1963<br />
Total A.2 A.3 and older<br />
100.0 69.2 30.7<br />
Spawning Spawning migrants Spawning migrants<br />
migrants Number per cent Number per cent<br />
Number . of A.2 of A.2<br />
5,0 . 3,0 4,3 2,0 6,5<br />
10,0 6,0 . 8,6 • 4,0 13,0<br />
20,0 . 12,0 17,3 8,0 26,1<br />
30,0 18,0 25,9 12,0 39,1<br />
40,0 24,0 34,6 16,0 52,2'<br />
1.1.1•■■•••••••■■•••••••■.r.+1•■•■•■■••■•••••■■■•■■■•■•■<br />
The age determinations in Januaxyof the years 1958 to 1963 showed<br />
on an average.69.3 per cent of salmon of the sea year class A.1+ (fish of<br />
two winters) and 30.7 per cent older fish. In contrast to this the percentages<br />
9 The sea year class that is designated as A.2+ at the time of spawning<br />
(November) is identical with the class A.1+ that occurs in the sea.
- 84 -<br />
of the corresponding sea year classes in the spawning swarms amounted to<br />
about 60 and 40 per cent, respectively. If we now vary the number of the<br />
salMon emigrating from the Baltic Sea and calculate with the aid of the<br />
above figures their percentages in the sea year classes in the Baltic Sea,<br />
we obtain the values listed in Table 21. It.is seen that, although the<br />
number of spawning migrants of the sea year class Ai2 is always, higher than<br />
that of the older Salmon, their Share in the sea year class A.2 of the<br />
stock in the Baltic Sea is, however, smaller. In other words: the percenr.<br />
tage of salmon of the sea year class A.2 that migrate is smaller than that<br />
of the class A.3, numerically there are, however, more because the number<br />
of the younger fish is always preponderant. After thia result there is no<br />
* longer a dïfference .as far as the matter itself is concernedii although it<br />
is not possible to carry out a quantitative comparison. *<br />
One can therefore say that salmon that have a fat content of<br />
at least . 12 per cent in the spring and a mean diameter of the oocytes of<br />
more than 1.5 mm will probably spawn in the fall of the same year.<br />
. 3.3. The fertility of the salmon<br />
For the investigations of the fertility have been used in gen-<br />
eral fish that were in the maturity stage V. With the discharging ovaries<br />
been.<br />
it is possible that some eggs have already/deposited. On the other hand,<br />
it is sometimes difficult to distinguish between recruitment oocytes and<br />
maturing oocytes during the earlier stages of maturation. Furthermore,.<br />
V. D. Vladekov (1956) points out for Salvelinus fontinalis that more mat-<br />
uring oocytes differentiate than there are mature eggs later. Because all<br />
the oocytes when fully developed would not have enough room, some are<br />
being resorbed.<br />
B. Carlin (1951), A. Lindroth (1952) and Jokiel (1950 give<br />
11). 277]
- 85 -<br />
the relative amount of eggs in the salmon for practical use. The mean<br />
values vary for different Swedish rivers from 1060 to 1400 eggs per kg<br />
salmon, in the Vistula the valùes lie around 1400. The correlation coef-<br />
ficient is 0.6624 for the Ulme-Xlv, 0.7512 for the river Ljusnan. B. Carlin<br />
(1951) calculated a linear relation between number of eggs and weight of<br />
salmon for fish weighing 2 to 14 kg.<br />
With the aid of very careful statistical analyses, J. A. Pope,<br />
D. H. Mill's, and W. M. Shearer (1961) have treated the fertility of the<br />
Atlantic salmon.. The fish investigated were substantially smaller than the<br />
Swedish salmon and had lengths of 47.5 to 95.0 cm, average 70 cm (about<br />
3.14 kg). Pope et al. found that the changes in the number of eggs oan be<br />
traced to 75 per cent of the different lengths of the fish and only to 7<br />
per cent to the weight of the salmon. The changes in the condition of the<br />
salmon during the upstream migration are reflected in considerable fluct-<br />
uations'in weight. There.does not exist a linear relation between number<br />
of :. eggs and weight of the salmon.<br />
Acording to the authors cited, the relation between length and<br />
number of eggii can be expressed best through the allometric growth formula<br />
N = cL b , where N is the number of eggs, L the length, and c and b are con-<br />
stants. According to . the investigations of Pope et al., b appears to be a<br />
universal constant of the magnitude 2.3345. On the other hand, c character<br />
izes probably the influence of the environment. Annual differences in the<br />
values for one river were not significant, but there were significant dif-<br />
ferences between individual rivers. The above formula can be used generally .<br />
with an error of ± 10 Per cent. Since the fertility can vary significantly<br />
between individual rivers,'we have to expect a priori a greater scattering<br />
• [P. 278 1<br />
of the individual values. for egg .counts of sample catches in the sea than
10000<br />
5000<br />
I_ •<br />
N. 0,622 L 2' 3345<br />
20 a ,60 6o ao 00 m uocyili.tin ge)'<br />
Length<br />
Fig. 23. Number of eggs as function of the<br />
length in the Baltic Sea salmon.<br />
- 86-<br />
those of the rivers. In Fig. 23 are shown the numbers of maturing oocytes<br />
in 40 salmon from the Baltic Sea in relation to the fork length. On the<br />
basis of the allometric growth formula and the value b = 2.3345, the ecol-<br />
ogical constant c was calculated as 0.662, a value that agrees well with<br />
the results of Pope etaal. For lengths under 80 cm the values differ from<br />
those - of the formula N = 0.662 L 2 ' 3345 that is used as basis. It has<br />
15000<br />
EizaN(N) Number of eggs<br />
already been pointed out that perhaps not all the maturing oocytes develop<br />
into mature eggs..It must therefore be assumed that the number of the mat-<br />
uring oocytes agrees the bettèr with the final number of eggs; the higher<br />
is the the state of maturity attained. As has been shown, one can expect<br />
that most of the smaller (ïounger) individuals,attain maturity only a year<br />
later than the larger (older) fish. In the fish over 80 cm long the recruit-<br />
ment oocytes and the maturing oocytes are already very clearly differen-<br />
tiated. It is therefore easy to understand thitt the values for the<br />
smaller salmon do not correspond to the course of the curve that is demanded.
- 87 -<br />
The calculation of a formula for the fertility cannot have any<br />
special importance on account of the very large scatter of the values. It<br />
. will be more useful to follow theppeetical usage and to state the number<br />
of eggs per kg weight of the salmon. It is only possible to give an approx<br />
imate figure for the present data, because no individual weights are available.<br />
The numbers of eggs fluctuate between 700 and 1700 and are on an average<br />
about 1200 per kg fresh weight.<br />
4..•<br />
The migration of<br />
the Baltic Sea salmon<br />
When one speaks about the migrationS of fish, one generally<br />
•means that they Occur periodically at certain times at certain places.<br />
This frequently concerns the formation of spawning assemblies. Tagging<br />
has provided information about the extent and boundaries of the population<br />
area as Well as about the general direction of the migration at certain •<br />
. seasons. One can, however, not say what places the fish has been visiting<br />
between release and recovery and one does not know anything about its non-<br />
periodic changes of place.<br />
In the Atlantic salmon likewise nothing is known *about the non»<br />
periodic movements. After the fish have left the freshwater it is dif-<br />
•ficult to follow their migration, eSpecially in regions of the open ocean,<br />
where no special salmon fiehery in being carried out. One assumes that<br />
the salmorrof northwestern Europe have their feeding grounds to the north<br />
and west of the British Isles and between Iceland and Greenland (K. A. .<br />
'Winch 1955). On the other hand, Huntsman (1948, after K. A.Pjeinch 1955)<br />
says that the salmon do not leave the area of influence of their rivers.<br />
• He considers longer wanderings to be only exceptions.
- 88-<br />
Through the extensiveSvedish tagging activities we are better<br />
informed about the movements of the salmon of the Baltic Sea, which form<br />
their own stock and which are in general confined to the largely selfcon..<br />
tained Baltic Sea. However, here also elnr knowledge has been augmented,<br />
especially of the periodic migrations. EVen tagging is of little help in<br />
the investigation of local movements. .<br />
For a third kind, the extended journeys, we have only few, but<br />
interesting data. In this connection the region of Sukkertoppen (western<br />
Greenland) plays a special role. There five salmon have been caught that<br />
had made long journeys. They had been tagged and released in Scotland,<br />
Canada, and England (J. Nielsen 1961) and in western Sweden (B. Carlin<br />
[P. 279] .<br />
1962b). The longest jOurney had been made by a Swedish salmon from a trib-•<br />
utary of the river Xtran, which travelled over goo° km. J. Nielsen (1961)<br />
could demonstrate that a large part of the salmon of the Sukkertoppen dis-<br />
trict are . not Greenlandic salmon, but must have immigrated from other aream.<br />
Irish taggings (A. E. J. Went 1956, E. Twomey and A. 0 1 Riordan<br />
1963) showed that the salmon remain mostly in the region of the island.<br />
However, some fish travel as as far as the Scandinavian coast. One recap-<br />
ture has been reported at a distance of 1750 km near Xngelholm (southern<br />
Sweden). Corresponding results were obtained by B. Carlin (1955) with<br />
tagging in the river Lagan (southern Sweden). Most of the fish were .caught<br />
off the coast of southern Sweden and off the coast of southern Norway.<br />
Three recapeires could be reported from the British Isles and two from.<br />
northern Norway.<br />
The salmon of the Baltic Sea are not known to leave their home<br />
area. Only very few young salmon do wander during their first year in the<br />
• sea as fax as the Belt. For the remainder the western boundary of their
- 89 -<br />
area of distribution is formed by a line between Regen and Schonen accor-<br />
ding to Swedish,Finnish,.Polish and German taggings.<br />
4.1. The divisions of the periodic migration<br />
• The periodic migration is determined by the life cycle of the<br />
salmon. It takes place in three divisions, the emigration from the river,<br />
that is connected with the transformation into the smolt stage, the search<br />
for food in the Baltic Sea and the return to the home stream during the<br />
spawning migration.<br />
4.1.1. The migration of the smolt<br />
K. A. Pyefinch (1955) calls the transformation into the smolt<br />
stage a series of morphological and physiological changes. The most striking<br />
external phenomenon is the change. from the "trout type" (parr) into the<br />
"silvery fish" through deposition of guanin. The physiological process of .<br />
the transformation into the smolt stage is not yet completeliunderstood,<br />
although werk on the ion budget and the components of haemoglobin (H. Koch<br />
1963), the activity of the glands (Hoar 1953, Fontaine : 1954, after7 Pyefimàh<br />
1955) and the action of hormones (D. H. Piggins 1962) have provided partial<br />
knowledge.<br />
With reservations one can at present consider the process of<br />
the transformation into the smolt stage to take place about as follows.<br />
(various authors, according to W. S. HOar 1957).<br />
When the parr have attained a certain size, internal changes<br />
take place that trigger the process. There is agreement that during this<br />
period the thyroid plays a role by causing the deposition of guanin and<br />
'influencing processes of morphogenetic growth. D. J. Piggins (1962) suc-<br />
ceeded in increasing the number of, young salmon capable of emigrating<br />
(smolts) by feeding bovine thYroids. However, W. S. Hoar (1957) attributes<br />
r
- 90 -<br />
the initial effect to'the hypophysis, which controls not only the growth<br />
but also the function of the thyroid. In this connection the hormone som-<br />
atotropin appears to be of great importance,Secause it regulates growth<br />
and in low concentrations raises the tolerance for salt. There is therefore<br />
the possibility that the changes in the hypophysis-thyroid system result<br />
in a mineral imbalance that can be compensated only in an environment with<br />
a higher salt content. This means then that the smolt has not to tolerate<br />
the higher salinity as a disturbance of its physiological state, but that<br />
it needs it in order to remove an existing disturbance.<br />
When the transformation into the smolt stage has.taken place,<br />
the beginning of the emigration must be stimulated through various environ,<br />
Mental factors. H. C. White (1939) does not consider rain or high water<br />
levels to be decisive, but temperature increase and the amount of light<br />
intensity. G. Alm (1934) also considers the temperature to be important.<br />
'After they have reached the region of the river mouth, perhaps<br />
in May/June, the smolt from the rivers of the Gulf of Bothnia remain in<br />
a transitional area for a short while (days or weeks). A more rapid growth<br />
begins already at this time. The fish probably eat.insects that live on<br />
the surface of the .water (A. Lindroth 1961b). Their movements are still<br />
non-directiOnal and do not extend fax. During the course of . summer and<br />
fall they colonize the Gulf of Bothnia during the transition into the post-<br />
smolt stage.<br />
4.1.2. The feeding migrations<br />
In Table 22 have been assembled and recalculated some results<br />
of tagging experiments from the Indalsglv and the Lulegiv (B. Carlin 1959a,<br />
1963) and from the Oulujoki (E. Halme 1961). The number of reports of re-<br />
boveries has been given for the different periods and the three regions<br />
[P. 280]
- 91 -<br />
as percentages of thé recovery reports from all three regions (Gulf of<br />
Bothnia, Gotland, southern Baltic Sea). In this manner it will be possible<br />
to recognize the migrations of the. salmon.<br />
The Indalsâlv is a Swedish river in the central region of the<br />
Gulf of Bothnia; Luleâlv (Sweden) and Oulujoki (Finland) run into the nor-<br />
thern part of the Gulf of Bothnia. About 50 per cent of the salmon from<br />
the Indalelv were caught during the first year after release in the Gulf<br />
of Bothnia, for the Oulujoki this figure was more than 90 per cent. The<br />
differences between the two regions, are still apparent in the second and<br />
third year after release, when a larger part of the tagged fish has mig-<br />
rated into the other two regions. There are no fundamental seasonal dif-<br />
ferences between the areas. The most numerous recaptures are made in the<br />
Gulf of Bothnia during July/August on account of the spawning migrations.<br />
During the cold season, when the Gulf of Bothnia is covered with ice,<br />
most of the recapture reports côme from the Baltic Sea proper.<br />
The results in Table 22 make clear the following: the salmon<br />
of the northern zone (Gulf of Bothnia) remain for more than a year in the<br />
Gulf of Bothnia, before a part of them move into the Baltic Sea proper.<br />
In this they are being joined by the salmon of the Gulf of Bothnia that<br />
are a yeax younger. The majority of these fish remain in the northern waters<br />
only until the late summer'of the first yeax. The occupation of the Gulf<br />
of Bothnia and of the Baltic Sea proper appears to be connected in part<br />
with the current conditions. The Swedish as well as the Finnish salMon<br />
move with the cuxrent along the Swedish coast of the Gulf of Bothnia to<br />
the south. To the north of the Illandsea the water masses are being deflected<br />
by the influence of the topography partly to the east and finally to the<br />
north and then flow along the Finnish coast. A number of salmon that
changes annually appears to follow this current, whereas others reach the<br />
Baltic Sea proper by way of the Ilandsea. The further course of the migration<br />
can no longer be followed on hand of currents. Whereas the salmon frOm the<br />
rivers Lule and Oulujoki'remain predominantly around Gotland, a very large<br />
part of the fish from the Indalsâlv move into the soUthern Baltic Sea.<br />
Beginning with the second year, spawning migrants can always be found during<br />
July/August in front of the home rivers.<br />
Nothing has been known hitherto about the sojourn in the Baltic<br />
Sea. It appeared possible that the fish, after leaving the Gulf of Bothnia,<br />
searched out immediately the final feeding grounds and remained there, or<br />
that they move continuously during feeding and that they have no definite<br />
feeding grounds. In the end an annual round through the eastern Baltic Sea<br />
until the spawning migration had been assumed. Table 22 gives a weak hint<br />
as regards these questions. If the salmon of the Indalsev remain during<br />
Lp. 282]<br />
their sojourn in the Baltic Sea proper on an average farther to the south<br />
than the fish from.the Gulf of Bothnia, then not all can make a circuit<br />
through the eastern Baltic Sea . or wander annually around Gotland. In other<br />
words, a map that shows the recovered salmon within a limited period in a<br />
definite distribution in the entire Baltic Seà proper, does not indicate<br />
that every one of these salmon must have visited during its sojourn the<br />
various regions of the area occupied by the population. Even if a rather<br />
far flung migration is carried out; it is not to be assumed that those<br />
salmon who lived in the extreme south had been previously frequently in<br />
the far north or had moved there. This does not exclude, of course, that<br />
individual fish do not make lengthy wanderings.<br />
.<br />
A feW results of my own tagging experiments support this assump-<br />
'tion (Fig.'24 a'to c). In November 1960 15 salmon Were tagged near Bornholm,
Table 22. The recapture of tagged salmon in three differént.regions (north of 59 °N, 56 ° to<br />
59 ° N, south of 56 ° N) as percentage of the total catch in all regions.-<br />
(Recalculated after B. Carlin 1959 a, 1963; E. Reline 1961)1.<br />
Home river<br />
. Indalsâlv Luleglv .<br />
Oulojoki<br />
Age group Months - - 1954 1959 1959 1959 •<br />
59 ° 56-59 (,) 59 ° 59 ° 5 6-59 ° 56° - 59 ° 56-59 0 56° 59 0 56+59° 56 0<br />
V-VI 100 100<br />
. VII-VIII 100 0 86 14<br />
A.0 IX-XII 25 SO 25 81 5 14<br />
I-III 75 25 40 40 20 100 66 34<br />
IV-VI 11 22 67 - 29 43 , 28 100. 100<br />
A.1-A.3<br />
VII-VIII 80 11 5 88 12 95 5<br />
IX-XII 12 40 48 26 46 28 56 33 , 11<br />
I-III 11 89 7 35 58 31 35 " 34<br />
IV-VI 5 22 73 33 47 20 55 27 18<br />
A.0 Total i 48 27 25 92 3 5<br />
A.1 Total 14 20 66 26 • 46 28 58 28 14 47 35 18<br />
A.2/A.3. Total 17 32 51 - 32 30 38 61 26 13<br />
1 The percentage values of the sea year class A.0 are based on recaptures of 3 to 34, on<br />
an average of 12 salmon. The older classes are based on about 50 salmon.
•<br />
- 94 -<br />
of these six = 40 "Per cent have been reported hitherto. Pive of the fish<br />
had at the time of recapture not moved from the fishing ground 5 after a<br />
maximum of 12.months, one fish had migrated into the Lulettiv to spawn<br />
(Fig. 24 a).<br />
In the Danzig Deep 33 salmon have been liberated in November/<br />
December 1959 and in December 19 6 2. Of the fish recaptured at sea some<br />
.had not moved farther during 11 months than others in one month after re-<br />
lease. (Three fish of one experiment of February 1964 in the same area<br />
were recoverèd like the others in the Danzig Deep or off the Pomeranian<br />
coast, respectively.) Two other fish had migrated into the rivers Lule<br />
and Torne& after 7 and 19 months, respectively, in order to spawn.<br />
In a third experiment in November 1960, 52 salmon were tagged<br />
near Memel. Six of these fish have been recovered at sea. Of these four<br />
had moved into the Danzig Deep and two to Bornholm. A further six salmon<br />
were captured 7 to 8 months later during spawning migration in the rivers.<br />
Three of these were caught in the Gulf of Bothnia(lingermanalv and Indals-<br />
alv, respe-ctively) and three in the Bottenwik (Torne. and Kalix, respec-<br />
tively).<br />
Besides the spawning fish, no other fish have been recovered<br />
fn the three experiments that had moved north and crossed the 56th par-<br />
allel or had even reached Gotland. In the first experiment the fish had<br />
moved a maximum distance of 40 nautical miles from the place of release<br />
and had remained around Bornholm. The fish in the second experiment did<br />
not move farther to the south or to the west than 80 nautical miles and<br />
remained in the Danzig Deep or off the Pomeranian coast. Even in the third<br />
experiment there was only a maximum movement of 140 nautical miles after<br />
13 months. It cOuld not be established that the fish caught last had traV-<br />
eled the greatest distances.
•<br />
II><br />
Three conclusions can be drawn from these results:<br />
(1) The recaPtured salmon of the first two experimental series have carried<br />
out astonishingly short movements and have remained very close to the<br />
pdint of capture and release.<br />
(2) A large part of the recovered fish of the third experiment were cap-<br />
tured in the rivers.<br />
(3) The other fish of the third experiment had travelled the greatest dis-<br />
tances (a maximum of 140 nautical miles) and visited the Danzig Deep<br />
as well as Bornholm.<br />
These results support the conjecture that the salmon do not make<br />
far flung travels or annual periodic movements once they have reached the<br />
Baltic Sea proper. One has rather to assume non-periodic local movements<br />
after the fish have reached a feeding ground. This will be investigated later.<br />
4.1.3.<br />
[P. 286]<br />
In the third experiment mentioned above the high percentage of<br />
spawning migrants is striking. At the time of tagging these fish were res-<br />
iding in the Baltic Sea in their second year (A.11-) and they did spawn in<br />
the course of their third year. Since of the total catch only the smaller<br />
fish (under 75 cm fork length) have been tagged, it is possible that of<br />
the remaining fish still more than one-half did migrate to spawn. Con-<br />
sequently one could explain the results of this tagging as follows:<br />
A few salmon in the southern Baltic Sea, of which the majority<br />
did spawn a year later, had moved in November 1960 already to the west of<br />
Memel. When the maturing fish wandered in the spring of 1961 towards their<br />
home rivers, the juvenile fish returned in part to the Danzig Deep and in<br />
part to Bornholm. In any case it must be stated that the sPawning migrants<br />
associated in the fall before their spawning migration still with juvenile<br />
- 95<br />
-
•<br />
66<br />
65<br />
64<br />
63<br />
62<br />
61<br />
60<br />
59<br />
58<br />
57<br />
56<br />
55<br />
54<br />
Recapture of tagged salmon. Released<br />
near Bornholm, Nov. 1960.<br />
- 96 -<br />
[p. 283]
•<br />
6<br />
65-<br />
64 -<br />
62-.<br />
61 -<br />
6<br />
. 5<br />
.<br />
591-<br />
576<br />
5<br />
55<br />
$4<br />
•<br />
1 1 I_ _I_ 1 _I<br />
10 15 20<br />
Fig. 24 12. Recapture of tagged adult salmon.<br />
the Danzig Deep, Nov./Jan. 1959, Dec. 19 6 2,<br />
/'<br />
f<br />
1 .<br />
25<br />
Released in<br />
Feb. 1964.
•<br />
66<br />
65<br />
64<br />
63<br />
62<br />
61<br />
60<br />
58<br />
57<br />
56<br />
55<br />
54<br />
10 15 20 - 25<br />
Fig. 24 c. Recapture of tagged mature salmon. Released<br />
near 14emel, Nov. 1960.<br />
- 98 -<br />
[P. 285]
•<br />
- 99 -<br />
fish. The tagging does not give any information about the course of the<br />
later movements until the fish ente r . the home stream. We do know, however,<br />
through the analyses of the stock, that the age composition changes each<br />
year beginning in April/May on account of the emigration of the spawning<br />
fish. This is also clearly indicated by the reduction in the average weight<br />
(Table17). The change caused by the emigration of the larger fish extends<br />
into June.,(There are n4 data for July on account of the cessation of the<br />
fishing.) It is, however, not known that the share of the large fish does<br />
increase at this time On the fishing grounds 4 or 5, which have to be<br />
crossed by the maturing fish.<br />
Table 23. Number of salmon of more than 5 kg weight<br />
on various - fishing grounds as percentage of<br />
the total catch.<br />
Bornholm<br />
Month 58 .5.2 (60) 61 Mean 58 .52 60 61 Mean<br />
59 60 (61) 62 59 60 61 62 •<br />
Nov./Dez. 60 55 (27) 29 48,0 37 31 38 19 31,3<br />
Jan./Febr. • 55 31 (44) 26 37,3 41 36 24 13 28,5<br />
MârziApril 39 15 10 21,3 36 21 40 31 32,0<br />
On the Pther hand, Table 23 indicates that the share of the fish<br />
over 5 kg in weight in the catch near Bornholm diminishes during the course<br />
of the season. This phenomenon could perhaps be explained by the beginning<br />
of the emigration of maturing salmon.<br />
Danzig Deep<br />
Many papers have been published about the "homing" of the sal-<br />
mon about to spawn. Especially important are the results of A. D. Hasler<br />
(1954, 1960), who could demonstrate a "sun-compass mechanism" and, among<br />
other things, a long-persisting olfactory memory in Pacific salmon. J. B.<br />
Brett and C. - Groot (1963) speak of the innate ability in sockeyesalmon<br />
(Oncorhvnchus nerka) to be able to keep s8..u. sun-compass diredeon and they
River Ap. May Jne. Jly. Aug.<br />
Tornea 25 ' 74<br />
• Lima 4f 55<br />
Dal 23 64 12<br />
tvliirrum 6 35 35 23<br />
- 100-<br />
attribute to it.a rythmic sense that is attuned to diurnal periods. Accor-<br />
dingly one reckons today with the ability of the maturing salmon to orient<br />
themselves at sea with the aid of their "biological clock" and the sun until<br />
they perceive the emell of the home waters. After this they find their waY<br />
by their chemical sense organs. These abilities enable every individual<br />
salmon to attain the goal of its travels quite independently of its com-<br />
panions. This leads to a behaviour that is different from that known in<br />
gregarious fish (e.g., sardines). In the clupeids the reaction of the in-<br />
dividual is governed largely by the behaviour of the school. From this point<br />
[13 . 287]<br />
of view it is perhaps not appropriate to talk about a "spawning school" of<br />
salmon. It is certain that the common time of migration and the same goal<br />
brings the fish together gradually; the movements of the individual fish,<br />
however, are determined through the individual orientation. This behaviour<br />
Table 24. Monthly yields of may be a cause of the fact that no large<br />
salmon in Swedish rivers as<br />
percentage of the annual catches are made during the migration of<br />
catches.<br />
the salmon into the rivers.<br />
The monthly yields of salmon in<br />
the Swedish rivers have been assembled in<br />
Table 24. From this it can be seen that<br />
the rise of the salmon into the rivers of<br />
the Bottensee takes place during May to July and in those of the Bottenwik<br />
from June to July. When the salmon of the southern Baltic Sea begin to<br />
migrate between April and June, then they have not much time left to reach<br />
their home river. Oné can therefore assume that the spawning migration is<br />
being carried out rather fast. Travelling speeds of 100 km/day have been<br />
, observed in salmon ready to spawn (Suvoràv 1959) . Nothing definite is known<br />
about the routes of travel of the maturing salmon. E. Halme deduces from
- 101 -<br />
tagging experiments'that salmon from the Oulujoki return along the Finnish<br />
coast of the Gulf of Bothnia.<br />
4.2. Local movements<br />
In general we must assume that the hourly and daily movements<br />
of the salmon in the Baltic Sea are determined by the search for food. There<br />
can be no doubt that these local movements are of the utmost interest for<br />
the practical fishery, because they are the cause of the short-period<br />
fluctions in the yield. The ascertaining of such local movements and of<br />
their immediate causes requires, however, an extensive material that can<br />
be obtained only with difficulty. If we want to learn more about the causes<br />
of these local movements, we have to have recourse to the results of the<br />
critical examination of the captures per unit effort. We could start from<br />
the fact that the catches can be influenced on the one hand by the specific<br />
effects of the fishing gear and on the other hand by environmental factors.<br />
The latter have the effect to induce the salmon to stay at certain places<br />
or to travel. We found such factors to be:<br />
(1) temperature,<br />
(2) wind conditions,<br />
(3) competition for food,<br />
(4) occurrence of cod.<br />
We can neglect the temperature conditions because they lead to<br />
seasonal vertical movements of the salmon. The catches with nets are af-<br />
fected only by the wind conditions, the line catches, on the other hand,<br />
are affected by all other factors. If we now enquire which of them can<br />
cause local movements of the salmon, we are left with only the food and<br />
perhaps also the wind conditions and currents.<br />
It has already been pointed out that a pelagic gregarious fish,<br />
•
IS° 16°<br />
- 102 -<br />
the sprat L is, besides other animals, the most important food of the<br />
salmon. These clupeid, in turn, feed , on plankton. The starting link in<br />
1.1).288]<br />
this chain is represented by the primary producers, the phytoplankton,.the<br />
production of which is governed by the nutrients. The nutrients as well<br />
as the plankton and to a large extent also the sprat are dependent in their<br />
occurrence on water currents (which are mainly wind-driven in the Baltic<br />
Sea proper) and of their discontinuities (divergencies, etc.). It is also<br />
clear to assume an influence of the wind on the offer of food. Even if we<br />
cannot define exactly a connection between wind conditions and the occur-<br />
rance of salmon, an indirect relation may be assumed (see 2.3.3.2.). In<br />
this connection an example may be offered that can also give other infor-<br />
mation.<br />
Fig. 25. Fishing positions of salmon cutters south<br />
of Dueodde, Febr. 22 to March 4, 1962.<br />
From February 22, 19 6 2 on, a fleet of six to ten vessels was<br />
.fishing with driftlines on a fishing ground south of Dueodde near the
- 103-<br />
Renne Bank in about 60 m depth of water (Fig. 25). During the first three<br />
days stormy northeast winds prevailed, followed by east winds that sub-<br />
sided after February 27. Between March 1 and 4 light winds from various<br />
directions prevailed.<br />
During the period of the northeast storms and the east storms<br />
it was possible to fish only with lihes. The captures per unit effeort<br />
were more than 20 salmon per 1000 hooks and thus rather favourable, but<br />
they dropped with the diminishing winds to fewer than ten salmon per 1000<br />
hooks. The favourable winds allowed to employ driftnets beginning on March<br />
1, 1962. The Catches amounted to 130, 40, 5, and 2 salmon per 100 nets<br />
between March 1 and 4 and. yielded on March 1 a total of almost 1500 fish<br />
(Table 25).<br />
It cannot be established with certainty whether the large num-<br />
bers of salMon were present on the fishing grounds prior to March 1, when<br />
lines were still used for fishing. It must, however, be assumed that in<br />
that case the catches with lines would have been much greater. It is thus<br />
very probable that the fishing on March 1 encountered a very numerous<br />
acktkes<br />
group of salmon that happened to pass through at that time. The -e-etp-tttre-e<br />
[P. 2891<br />
per unit effort show that on the second day only stragglers were still<br />
being caught. On March 1, the catch amounted to 30 salmon per 1 km 2 of<br />
fished area, on March 4 it was only 0.45 salmon.<br />
Let us attempt to draw a conclusion from the known facts in<br />
regard to the behaviour of the salmon.<br />
The fishermen had taken up their driftlines on the afternoon<br />
of February 28. These had been set out around 0400 h in the morning and<br />
had yielded on an average 6.9 salmon per 1000 hooks. In the afternoon the<br />
wind had dropped so much that already at sundown of the saine day it became
•<br />
•<br />
- 104 -<br />
possible to begin with putting out nets. After about 12 hours the gear<br />
was on board again the next morning.and had caught on an average 130 salmon<br />
per 100 nets. About a further 12 hours later the driftnets were in the water<br />
again and yielded until the next morning 40 salmon per 100 nets. The first<br />
travelling salmon were swimming in large numbers across the fished area<br />
at the earliest on the evening of February 28 and at the latest around<br />
midnight. The swarm may also have persisted during the day on March 1. The<br />
number of fish, however, did decline, because on the next morning only 40<br />
salmon were caught per 100 nets. On March 2 the swarm had definetely passed,<br />
because the catch during the following night yielded only 5 salmon per 100<br />
nets. In its longitudinal grouping the swarm had such a shape that the<br />
salmon were concentrated most densiely at its front in the direction of<br />
travel.<br />
Let us also attempt to learn something about its lateral com-<br />
position. The catch of 130 salmon per 100 nets or of almost 1500 fish per<br />
1 km 2 of fished area constitutes a rare event in salmon fishery. It leads, •<br />
however, easily to the unwarranted conception that the salmon had travelled<br />
in a very dense swarm. The best catches, however, brought only 1.7 to 2.0<br />
salmon per net, the emallest 0.2 to 0.4 fish. This means that the fish were<br />
caught by the nets in such a manner that they were at a least distance of<br />
on an average 12 to 14 m and at a greatest distance of 60 to 120 m from<br />
one another. We cannot assume that the fish had been swimming in a line<br />
[P. 29 0 ]<br />
and so got caught simultaneously. That means that the salmon were swimming<br />
in the water at inter -ials of more thenan average of 12 m. On the other<br />
hand.one cannot reckon that all fish were caught that encountered a fleet<br />
of nets. Thus there were more fish present than were caught and they must<br />
have been travelling closer together.
•<br />
9:1<br />
0<br />
a)<br />
el-4<br />
o<br />
(XI<br />
-P<br />
CNI<br />
4-<br />
o<br />
4-,<br />
\<br />
crs<br />
0<br />
P<br />
■,<br />
0<br />
CD<br />
o<br />
CH<br />
•ri<br />
(/)<br />
•H<br />
ro<br />
Ei<br />
<br />
o<br />
Si<br />
N<br />
sO<br />
en • rci<br />
*.g<br />
,1<br />
Fi<br />
tn<br />
0<br />
Cr3 -1?<br />
N. •• cr," s.o<br />
9<br />
.ul E u,<br />
1-4 •4-<br />
•<br />
- 1 06-<br />
catches of Pacific Salmon, considers an aggregation of four to six fish<br />
as a great school, whereas he calls . the appearance of two fish together<br />
a normal size of a school. Such relations are quite applicable for the<br />
Baltic Sea salmon. It happens frequently that several salmon are caught<br />
in one or two nets and that only after a distance of 500 or 1000 ,m there<br />
will be again some salmon in a net. Good orexceptional catches are ex-<br />
perienced Only when a number of these small groups come together.<br />
In the present case it is not possible to state with certainty<br />
the causes for the concentration of the fish. There were no observations<br />
by echo sounder of the occurrence of food fishes. Let us therefore ex-<br />
amine the wind and current conditions on the fishing grounds (Fig. 25,<br />
Table 25). The northeast and east windstorm that prevailed since February<br />
22 undoubtedly caused a damming of the water against the east coast of<br />
Bornholm, which resulted in a current directea to the southwest. Under<br />
the influence of the topographical conditions it is possible that the<br />
water became dammed again in front of the Renne Bank and the Adlergrund<br />
until the dropping of the wind made it possible for the water to flow<br />
to the south and east. During the first phase several smaller groups of<br />
salmon may have been conveyed to the coast of Bornholm by the wind drift<br />
where they were thrown together by the damming and from where they then<br />
drifted with the current towards the south. In the case depicted we thus<br />
had a. relatively large and.fast-moving group of salmon that had been formed<br />
perhaps under the influence of the wind conditions and of the topographical<br />
relations. Under these Circumstances it cannot be excluded that there were<br />
also schools of clupeid present that behave much more passively in relation<br />
to currents than the. salmon.<br />
In other cases the wind can hardly have played a role, as is
14,3<br />
14,3<br />
30,7<br />
31,3<br />
27,7<br />
6,0<br />
15,0<br />
104,3<br />
47,5<br />
50,0<br />
4,3<br />
2,4<br />
j9,1<br />
34,9<br />
96,5<br />
156,0<br />
32,1<br />
10,7<br />
43,7<br />
10,5<br />
- 107-<br />
shown in Table 26. The results of line fishinir near Memel during January<br />
and the beginning of February in weather with light to strong winds had<br />
been fair. When it fell almost calm, the net catches between February 7<br />
and 9 became very good and after a short-lived recession they became even<br />
excellent. Four days later the fleet had moved 30 to 40 nautical miles<br />
farther south into the Danzig Deep. There excellent line catches were made<br />
for a few days with rapidly increasimg westerly wind storms. Unfortunately,<br />
there are-no exact records of positions and echo soundings. It is, however,<br />
certain that in regard to the net catches neither the preceding light winds,<br />
nor the light winds prevailing during the fishing with nets had any con-<br />
[p. 291]<br />
nection with the excellent results. It is therefore probable that the presence<br />
Of food fish played a role here.<br />
Table 26. Salmon fishery in FebrUary 1959 near Memel<br />
and Briisterort.<br />
Febr. Number<br />
of Wind<br />
1959 Cutters<br />
1.<br />
2.<br />
6 N W. 2-.6<br />
West of Memel<br />
80-75m water depth<br />
Salmon Salmon<br />
1000 hooks 100 nets<br />
7,3<br />
43 . j<br />
5.<br />
6:<br />
7.<br />
8.<br />
9.<br />
10.<br />
11.<br />
12.<br />
13.<br />
14.<br />
15.<br />
16.<br />
17.<br />
18.<br />
19.<br />
p20.<br />
21. .<br />
22.<br />
23.<br />
24.<br />
25.<br />
5<br />
4<br />
2<br />
2<br />
2<br />
2<br />
2<br />
3<br />
3<br />
3<br />
2<br />
I<br />
1<br />
4<br />
4<br />
1<br />
3<br />
5<br />
4<br />
5 .<br />
W3 6,6<br />
Stale = C8,1111 4,3<br />
um1 ' =<br />
S<br />
variable<br />
1<br />
Si<br />
Si<br />
SO 1<br />
SO 1<br />
SOI<br />
S2<br />
SW 4 .<br />
NNW 4<br />
SW 6<br />
W5<br />
W6<br />
W8<br />
NW 8<br />
NW 6<br />
NW 3<br />
W7<br />
W4<br />
West of<br />
Brasterort<br />
100m w.d.<br />
Salmon<br />
1000 hooks
•<br />
- 108-<br />
This cause certainly must have affected the catches on the<br />
Mittelbank in April 1963. There the best catches were made in depths of<br />
20 to 30 m. The salmon could even take up hottom-dwelling food animals.<br />
According to the statements by the fishermen they had eaten besides stickle-<br />
backs also sprat and small crustaceans (Table 27).<br />
Table 27. Salmon fishery in April As a final example will be<br />
1963 on the southern Mittelbank. discussed the catches in the Danzig<br />
Apr. Number Aver. Salmon Bay of February/March 1964 (Table 28).<br />
of Wind depth per<br />
1963 cutters m 100mets- In contrast to the previous examples<br />
18.<br />
19.<br />
20.<br />
21.<br />
22.<br />
1<br />
7<br />
8<br />
6<br />
4<br />
umlf. 19<br />
unilf. 28<br />
NO 2 .„„,_28<br />
25<br />
turtIClableo<br />
23,2<br />
26,2<br />
13,7<br />
8,0<br />
3,9<br />
no exceptionally large catches were<br />
made there,.It was, however, possible<br />
to ascertain all attendant circum-<br />
. stances. During the entire period there<br />
were no fundamental changes in the wind conditions. The water was flowing<br />
continuously towards the south-southwest, as was shtwn by the anchored .<br />
cutters. Until February 28 the average yields were rather uniform at about<br />
3.3 to 4.5 salmon per 100 nets. Afterwards the catches increased and yielded<br />
on an average between 13.9 and 17.5 salmon per 100 nets from March 2 to 4,<br />
• [p. 293]<br />
only to diminish again later. The fish had eaten mostly benthic.amphipods<br />
and sticklebacks. Because the fish become often badly tangled in the net<br />
it is difficult to determine from which side each salmon has approached<br />
the net. In this case there appeared to have been no preference for one<br />
side of the net, so that no direction of movement could be inferred.<br />
, The available data give a picture that is entirely different<br />
from the.previous examples. The yields do not jump up suddenly, but in-<br />
crease slowly. Good.catches are made not only on a single day, but per-.<br />
sist for some time. With uniform current conditions and hardly changing
Table 26. Catches of salmon in the Danzig Bay, NNW of Kàhlberg, 45 to 82 m water depth,<br />
current WSW.<br />
February 19 64<br />
March 19 64<br />
24 25 26 27 28 29 1 2 3 4 5 Total<br />
Number of vessels 11 10 13 12 10 13 12 12 12 14 14<br />
Wind S03 S03 S03 SOS S4 SO 2 0 2 01 W3 W3 N4<br />
Salmon/100 nets 3,8 4,5 3,3 3,5 3,9 7,9 9,3 15,8 13,9 17,5 8,5<br />
Tot. no. of salmon 136 151 138 134 145 338 390 689 604 682 435 3841<br />
Tot. no. of salmon 704 338 279-i 3841<br />
Date<br />
Date<br />
Table 29. Food of salmon, March 1964,'Danzig Bay.<br />
Number of salmon Food per salmon<br />
examined with food MYsids Sticklebacks Clupeids Fish Ammodytes Reeds<br />
Number Number Number Number<br />
I. 3. 21 4 1,0 0,3 0,3<br />
2. 3. 75 16 0,5 1,0 0,4 0,1<br />
3.3. 54 9 4,5 0,7<br />
4. 3. 38 16 • 3,0 0,6<br />
5. 3. 26 6 • 1,0 1,5 0,2 0,2<br />
o<br />
%JD
winds, the data<br />
fishing grounds<br />
a while, eating<br />
the upper water<br />
• •<br />
•<br />
O<br />
29,I Lochs' goo Nitre<br />
18.3 LicAsellOONetze<br />
•<br />
S4MOn/100'netS<br />
•<br />
O 16,0 LachsellOONetze .•••<br />
o<br />
1..7 LachselICION•frp' ..'<br />
....• • "• •<br />
• e<br />
- 110-<br />
give the impression as if the salmon had arrived on the<br />
rather hegUeingly and gropingly. They remained there for<br />
during the - day benthic food in the depths and coming into<br />
layers at night. After a few days they moved on slowly.<br />
Fig. 26. Distribution of salmon in the Danzig Bay,<br />
March 2 to 4, 19 6 4.<br />
Let us examine the yields of March 2 to 4, which were the higheet,<br />
in more detail. InsFig. - 26 has been drawn a map of the distribution of the<br />
salmon based on the positions of the participating cutters and their cap-'<br />
tures per unit effort. According to this the greatest concentration of the<br />
fish occurred in the southeastern part of the fished area (25.4 to 34.4<br />
salmon per 190 nets). In the northern, eastern and southwestern parts the<br />
catches were not substantially higher than during the previous days (3.3<br />
to 8.9). From the centre of the distribution extends an area towards the<br />
north,-northwest with strongly scattered captures per unit effort, which,<br />
.however, were all higher than on the days before (8.9 to-27.2). From the •<br />
distribution in Fig. 26 can be deduced that. the area of strong scatter
- 111 -<br />
between Hela and Kahlberg represents either the route of inward movement<br />
or the route of outward movement of the salmon. Let us examine in this<br />
[p. 294]<br />
connection the positions of the.greatest concentrations of salmon be:4een<br />
March 1 and 5 (Fig.'27). The best results with an average of 14 salmon<br />
Fig. 27. Positions in the Danzig Bay where were made<br />
the best captures per unit effort between March<br />
1 and 5, 1064, with number of salmon per 100 nets.<br />
were obtained at the eastern edge of the fished area. The positions of the<br />
best catches remafned in about the same region during the next three days .<br />
(Fig. 26), whereas the centre of the greateet concentration of salmon had<br />
shifted farther to the west on March 5. These results suggest with great<br />
probability that the salmon were mOving from the northeast very slowly<br />
with the current into the Danzig Bay. During the day they prébably were. .<br />
feeding in deep layers of water on mysids and at night on the pelagic stick+<br />
lebacks. The salmon then .left the Bay gradually in the direction of Hela.<br />
Within four times twenty-four hours the group moved on an average Imam<br />
. than four nautiéal miles (seven km). Direction and velocity of this movement
•<br />
- 112 -<br />
must be considered to be the resultant composed of the daily periodical<br />
vertical movement and the horizontal feeding movement.<br />
In this connection it can be mentioned that among others 23<br />
tagged salmon (58 to 77 cm total length) were liberated on March 2. One<br />
fish, liberated at about 1400 h, was discovered two hours later in another<br />
net about 2 km distant, after it had swum in an easterly direction and<br />
passed a further fleet of nets.<br />
The findings about the local movements can be summarized as<br />
follows: the hoUrly and daily local changes during the period of feeding<br />
movements are determined by the search for food organisms and the pursuit<br />
of the prey. In addition they are probably connected with wind and current<br />
conditions. Such movements are indicated by sudden increases in yield that<br />
[p. 295 ]<br />
usually last only one or two days. On the other hand there is a gradual<br />
transition to the better catches that per:tee longer, these are caused by<br />
pure feeding wanderings.<br />
The salmon form generally.small groups of 2 to 10 individuals<br />
that may be encountered everywhere in the Baltic Sea proper. From time<br />
to time larger associations occur that are composed of several gmaller<br />
groups and that weie formed under the influence of food supply andwind-con-<br />
ditions. The single individuals are separated on an average by more than.<br />
10 m even in the greatest concentrations. The distances resulting from the<br />
local movements are never very large and probably do not exceed 10 km per<br />
day.<br />
In general it has been established that the salmon, in the same<br />
manner as the sprat approaches the coastal waters in the fall and spring.<br />
Apart from a probably daily vertical movement no periodicity of the local<br />
. movements could'be found.
•<br />
- 113-<br />
5 .. Age and growth of the salmon in<br />
the main basin of the Baltic' Sea<br />
For the determination of the individual growth of fish it is<br />
necessary to obtain the increase in length or in weight during a known<br />
period of time. That is possible in general only with the aid of tagging<br />
certain individuals. When it is . desired to ascertain the increase for a<br />
group of fish, then determinations of length, weight, and age are re-<br />
quired. On account of this close connection, age.and growth will be treated<br />
together in this chapter.<br />
5.1. On the terminology of age and growth analysesl °<br />
The numerous developmental stages of the salmon have had of old .<br />
definite names, especially in the English language. A small fish, freshly<br />
hatched from the egg is called "alevin" (yolk-sack brood)'. After the Yolk<br />
sack has been absorbed and after theflah begins.to feed, it.is.called<br />
"fry" (brood able to feed). During the following period of life, salmon<br />
have the outward appearance of trout and are designated parr until the<br />
transformation into smolt. Since the parr stage extends over several years,<br />
the additional terma "fingerling", "summerling", or one-yeax x-year parr:<br />
were introduced, according to the size and aee of the fish.<br />
In the post-smolt stage (for development of smolt. see 4.1.1.)<br />
the young salmon in the first year'in the sea ("speitzgen") are called<br />
"mielnica". Grilse (Jacob!s salmon) are those fish that spawn already<br />
after only two summers in the sea. Mentioned must be further the names<br />
"kelt" (a salmon thai has spawned, but preserved its nuptial colours)<br />
10 The essential deSignations have been taken from the paper by T. H.<br />
Aria and . W.-J. M. Menzies "The interpretat ion of the zones on scales<br />
of salMon...." (Rapp.Yroc., Vol. XCVII, 1936).<br />
,<br />
) •<br />
"
• and<br />
- 114-<br />
"mended kelt" (aealmon that has spawned, has a silvery colour, but<br />
is still in very poor condition, in German "lager").<br />
The transition from the life in the rivers to that in the sea,<br />
constitutes for the salmon a change that is penetrative in every respect.<br />
It has therefore been agreed to designate the age of the salmon by two<br />
symbols, A.B, which are separated by a full stop. "A" denotes the number<br />
of years spent in the river and "B" stands for the number of years spent<br />
in the sea. When at the time of sampling the year of life has not yet been<br />
completed, the full number of years is given with the symbol "+" added.<br />
If the fish has already spawned, the event will be indicated by inserting<br />
a "G" into the formula, whereby G counts for one year. A salmon with the<br />
age formula 3.2G1+ has spent three years in the river and two in the séa Lia. 29 6 ]<br />
before it migrated to spawn. After the return from the river it spent more<br />
than one year in the sea; it is thus over seven years old altogether.<br />
April 1 /B .-the key-day from which are counted the full years of life.<br />
Since we are treating priWcipally the life of the salmon in the sea, often only<br />
the number of years spent in the sea will be given. When we say that a fish<br />
belongs into the sea year class A.2, this means that this fish has spent<br />
already two years in the Baltic Sea since it emigrated from the river. We<br />
talk of age groups, when the ruiraber of years spent in both fresh water and<br />
in the sea has been given.<br />
5.1.1. The relation between total length and fork length<br />
ICEs<br />
During a session of (the International Council for Oceanography<br />
in 1933 it had been recommended to carry out the measuring of the length<br />
in salMon in such a manner as to give the fork length, that is,'the dis-<br />
tance between . the point of the snout and the central (usually shmefflt) ray<br />
of the tail fin. In contrast to this, fishermen and market employees use<br />
•
cm<br />
100<br />
80<br />
60<br />
40<br />
- 1 15-<br />
customarily the total length from the point of the snout to the end of<br />
the dorsal (mostly longest) ray of the tail fin.<br />
In order to be able to compare the two statements, we have<br />
taken both length measurements in 250 salmon and calculated the obvious-<br />
ly linear relation (Fig. 28). The measurement of the total length and of<br />
the fork length has been carried out in such a manner that they were based<br />
in every case on centimetres rounded off downwards. The fish of the group<br />
20<br />
50 ' m 90 lIC Lcm •<br />
Fig. 28. Relation between fork length (11.) end<br />
length (Lt ).<br />
•<br />
[1). 2971<br />
72 cm are thus on an average 72.5 cm long. This correction has been ap-<br />
plied in all oases before an evaluation was carried out. The statements<br />
given here.are all corrected values.<br />
total length Lt<br />
The following relation exists between fork length Lf and the<br />
Lf m -1.2256 0.9578 Lt<br />
t 1.2796 + 1.0441 Lf.<br />
L<br />
•
- 116-<br />
This result is based essentially on the measurements of salmon<br />
of length 60 to 110 cm, although also onfish of a total length of between<br />
40 and 60 cm. The equation contains an additive term. It is therefore not<br />
valid for the early stages. The measuring of such small fish" shows that<br />
the alevin with a mean length of 20,3 mm have not yet a forked tail fin,<br />
when they are freshly hatched. Slightly older alevins-showéd the forking<br />
of the tail fin already plainly with 26.62 fork length and 26.95 total<br />
length. In fry (brood without a yolk sack) the two measurements were found<br />
to be 28.08 and 29.05 mm, respectively. The difference between the two<br />
lengths is 1.2 per cent in alevin, 3.3 per cent in fry, 6.5 per cent in<br />
salmon of a length of 61 cm, and 5.4 per cent at a length of 100 cm, all<br />
Calculated as percentage of the total length. The percentage of the dif-<br />
ference thus reaches a maximum value and then diminishes linearly. On the<br />
basis of the knowledge of the developmental history wf,, can assume that the<br />
maximum value is attained in the smolt stage. This means that the equation<br />
given above is probably valid for the entire period of life in the'sea.<br />
5.1.2. The gutted weight<br />
Since the Danish and German salmon fishermen extend their fishing<br />
cruises to a maximum of 13 fishing days it is necessary to gut and clean<br />
the salmdn on board. Very many Swedish fishermen, as well as the Russian<br />
and Polish fishermen land their daily catches frequently whole (fresh weight<br />
= Wf). In order to make possible a recalculation from gutted weight to<br />
fresh weight and vice versa,'we have measured on board both weights in 34<br />
salmon. It appeared at first that the number of 34 salmon would be too<br />
gmall to calculate the relation between fresh weight and gutted weight.<br />
It was found , , however, that the relation is very tight, so that the values<br />
......■•••••■••<br />
11 The fish had kindly been put at my disposal by B. Carlin.
found can be used for the recalculation.<br />
- 117-<br />
Fig. 29 shows, as was to be expected, that a linear relation<br />
• exists that leads through the use of the method of least squares to<br />
W = -0.0241 + 0 .91 80 lélf<br />
Wf = 0.0263 + 1.0 893 Wg.<br />
Here W is the gutted weight and Wf is the fresh weight. The<br />
straight line does not pass exactly through the origin, but cuts the neg-<br />
ative abscissa. To be sure, we must expect this result, because one could<br />
'already speak of gutted weight'in case of an embryo, as soon as the ento-<br />
derm has been organized. The additive term, however, makes difficult the<br />
recalculation. We shall therefore examine how large is the error when we<br />
omit the additive constant and alter the slope constant correspondingly.<br />
The'equation then becomes<br />
W = 0.9114 Wf<br />
WÉ = 1.0972 Wg .<br />
Compared with the first equation, the recalculation from fresh<br />
weight to gutted weight results in an error of + 1.96 per cent for a fresh<br />
[1).- 298]<br />
weight of 1 kg, -0.20 per cent for a fresh weight of 5 kg, and -0.46 per<br />
cent for a fresh veight of 10 kg. The difference is thus largest for the<br />
'smaller salmon. For body weights between 1.6 and 20 kg the error lies below<br />
1 per cent, for those between 2 and 10 kg even under 0.6 per cent. On the<br />
fish markets the weight of salmon is given in the great majority of cases<br />
only within 100 g. This means that the error for these figures is generally<br />
higher than 1 per cent and is higher than 2 per cent for small fish. It is<br />
therefore justified for single recalculations to make use of the above<br />
simplified . relation and.to neglect the additive constant. One can proceed thus<br />
-Fresh weight = gutted weight + 9.72 per cent<br />
Gutted weight = fresh weight - 8.86 per cent.
W kg<br />
W 9 = -0 020 + (4919W,<br />
Fig. 29. Relation between gutted weight (W ) and fresh<br />
weight (Wf ).<br />
5.2. Materie and method<br />
15<br />
,<br />
- 118 -<br />
Age determinations have been made by examining the scales of<br />
the salmon. For this purpose complete.catches of the fish have been ex-<br />
amined in January of every year since 1958 on the Kiel Market for Sea Fish. \<br />
The length and weight of every salmon were ascertained and several scales<br />
were collected from every fish. According to a recommendation of he In-<br />
ternational Council for Oceanography) as far as possible, only such scales<br />
should: be used ihat are situated at the height of the posterior half of<br />
the dorsal fin above the lateral line. We have always taken the scales<br />
from this place, providing the salmon was not 'damaged there.<br />
The scales were treated in the following manner..They were<br />
first cleaned and examined under a stereoscopic microscope. Here speial<br />
A<br />
attention was paid to the sclerites developed during life in the rivers.<br />
We then selected the best scale and mounted it with others from fish of<br />
the sanie length on a slide. To finish the preparation, a second slide<br />
was fastened "over the scales. We now carried out the examination proper
v 0 00 0<br />
I I<br />
- 119-<br />
of the scales. Generally we used a binocular microscope at a magnification of<br />
40 to 150, but we have now switched to a scale projector “BT, Krauss,<br />
Paris).<br />
5.2.1. The arrangement of the scales<br />
In order to answer the question of where the first scales are<br />
being laid down on the body of a salmon, we have examined samples from 40<br />
positions on one side of the body of a salmon (Fig. 30)..With the aid of<br />
a scale projector we measured the radius from the centre to the uppermost<br />
margin of the scale (Fig. 31). It is found that the largest scales . are<br />
situated in the anal region closely below the lateral line. There is prob-<br />
ably the initial zone of scale formation. The next smaller scales are to<br />
be found in a band that extends from there below the lateral line as far<br />
as the pectoral fin. After this follow the dorsal and ventral regions of<br />
the body. The last scales are developed in the regions of the nape and of<br />
the throat, as well as at the stem of the tail.<br />
IBM Schuppenradius 92-M0 % der eel) fen Schteen<br />
= radius of = of the largest<br />
saie<br />
85 - 92% sa l es<br />
75 - 85%<br />
50- 75%<br />
25 - 50%<br />
Fig. 30. The size distribution of<br />
• the scales on the body of the<br />
salmon.<br />
In the largest scales the radius is almost four times as •<br />
P. 299]
- 120.-<br />
large as in the smallest. Winter bands and summer bands, however, are<br />
uniformly developed on all scales, so that in general the gmaller scales.<br />
also are suitable for age determinatibn. Therumber of the sclerites, how-<br />
ever, is very variable. Thus their number on the small scales is smaller<br />
by about one-fourth than bn the large ones. For comparative investigations<br />
the samples should always be taken from the same place. This is to be rec-<br />
ommended also for age determinations; because all irregularitieà on the<br />
scale that are the expression of various events, show up the more distinctly<br />
the larger are the number of sclerites.<br />
5.2.2. The significance of the sclerite rings for age determination<br />
It is to be the goal of the examination of the scales (W. J. M.<br />
Menzies 1925) to recognize the entire course of the life of the salmon,<br />
• because the essential events have left their traces on the scales. The pic-<br />
ture of the scale is formed by the sclerite rings, which are laid down con-<br />
currently with the entire process of growth. During sloweroWth, the rings<br />
are very close together, during fast growth they have greater distances be-<br />
tween them and at a sudden check the growth of the scales also ceases. The<br />
fundamental picture .of the scale is determined by the different growth in'<br />
fresh water and in salt water, as well as by seasonal effects. This makes<br />
it possible to ascertain the number of years of life, as well as to dis-<br />
tinguish the period in fresh water from that in salt water.<br />
[p. 300]<br />
This simple pattern, however, is being complicated by secondary<br />
effects, the causes of which .we do in general not know. Thus there appear<br />
frequently during the first summer in the sea cessations of growth, the<br />
so-called summer checks that cannot readily be distinguished from a winter<br />
band or annulus: . On the other . hand, the annuli.occasionally are lacking.
- 121 -<br />
The interpretation of the years in fresh w .- ter is especially difficult.<br />
On account of the slow growth in fresh water, the sclerites are lying<br />
much closer together than during the sea stage. It is therefore sometimes<br />
impossible to identify a period of growth with certainty. Occasionally<br />
Fig. 31. Scale of a salmon of a total length of 63 cm<br />
(A.Gr.2.2) (after B. Carlin).<br />
checks OCCUT durine—the first year in fresh water that are hard to dis-<br />
tinguish from true annual rings. It is therefore necessary to search always<br />
for aids that can support the age determinations and that confirm the in-<br />
terpretation and decisions of the examiner. The often cited "necessary<br />
experience" is doubtlessly important and useful. It can, however, play a<br />
role only when the experience is supported by measurable foundations.<br />
Such foundations can be obtained through tagging experiments. Such results<br />
are available only for the sea phase, whereas the results of tagging are<br />
very hard to.obtain for the life in the rivers.<br />
In the search for further aids we shall consider the sclerite
•<br />
•<br />
- 122-<br />
rings. M. N. Lishev (1958) demonstrated in salmon of the rivers in Latvia<br />
that there exists a clear relation between the.number of sciantes and<br />
the length of parr. There is supposed to be no relation between the age<br />
of the Parr and the number of sclerites. This statement is surprising.<br />
Since the length of the fish depends on the age and there is supposed to exist a<br />
clear correlation between length and number of sclerites,then the number of<br />
sclerites should depend also on the age of the salmon.<br />
In this connection let us examine a partial material of our age<br />
determinations of 1959 to 1961, which comprises 2756 salmon, and that of<br />
January 1962, which concerns 731 fish. In the first instance the numbers<br />
of sclerites were ascertained that were laid down during the first year<br />
Of life, in the second instance the numbers have been ascertained that were<br />
present after leaving the river. If one presents the average number of the<br />
sclerite rings in relation to the duration of the life in the river as a<br />
log-log graph for the first instance and as s simple graph for the second<br />
instance (Fig. 32) one obtains an approximately straight-line relation.<br />
The coefficients of correlation are<br />
r 1<br />
= -0.595 ± 0.0123 •<br />
r<br />
2<br />
= 0.642.± 0.0217.<br />
[1). 3 0 1]<br />
This means that the numbers of sclerites can perhaps serve as<br />
an aid in the age determination.<br />
The individual values, however, show a very strong scatter and<br />
à frequency diagram shows no gaps between the different age groups. It is<br />
therefore necessary to develop an artificial auxiliary model, in which the<br />
age.groups are separated more or less arbitrarily according to certain num-<br />
bers of sclerites (Table 30). When one divides the salmon according to this<br />
'method the following deviations are found from the age determinations. For
•<br />
- 1 23 -<br />
the age groups 2.B to 4.B the deviations from the age determinations are<br />
less than 5.6 per cent and those for the age group 1.B amount to 10 to 11<br />
Per cent. On account of the large deviations, the system cannot.be used<br />
for the 5L.year old smolt.<br />
M Skkriteazel<br />
im Jo&<br />
40<br />
2,0 4-<br />
log number of sclerites in the 1st year<br />
0,5<br />
1,0 In des Smoltalters<br />
45<br />
log age of smolt<br />
Fig. 32 a. Relation between the mean number of sclerites<br />
after one year in fresh water and the.duration of the total<br />
sojourn in the river (mean values of the age group).<br />
We have now to enquire whether deviations of 5 per cent or<br />
even 10 per, cent are permissible in our determinations. Doubtlessly, that •<br />
is not so. The data in Table 30. have, however, not been assembled in<br />
order to replace the investigation of age by the classical method, but<br />
1p.' 302]
•<br />
Sleritenzel<br />
im smoltistage<br />
Smair<br />
40 4-<br />
30 '<br />
20 +<br />
70 4-<br />
number of sclerites in<br />
- 124 -<br />
to make them easier. When there is any doubt in the determination whether<br />
a salmon has spent two or three years in fresh water before migration, the<br />
number of 14 sclerites after the first year or of 26 sclerites at the time<br />
of emigration indicates a smolt age of two years...A deviation of 5 per<br />
cent becomes thus effective only for fish to which the above pattern has<br />
been applied. To this must be added that one can use for orientation the<br />
number of sclerites after the first year in the river aswealas the number<br />
in the smolt age (at the time of emigration). This serves to reduce the<br />
possibility of an erroneous determination still further.<br />
2 3 4 5 Smoffler<br />
age or smolt<br />
Fig. 32 b. The mean number of sclerites<br />
in the smolt age in relation to the<br />
duration of the total sojourn in the<br />
river. (i4ean values of the age groups).<br />
It must be mentioned in this connection that the recalculation<br />
with the aid of the body-scale relation can provide important pointers for<br />
age determinations. A. Lindroth (1963a) has investigated in detail the<br />
growth of the scales as a special case of the relative growth of body<br />
parts. According to this, the scales of Parr show in all dimensions a
•<br />
L s - L c r s 0.85 Smolt Ls = length as smolt to be determined<br />
rc<br />
= length as parr to be determined<br />
Lp -t(<br />
Ls r-18) r<br />
s P Parr<br />
- 125 -<br />
weak tachyauxesis 12 ,' which is present in adult fish only in the vertical<br />
direction, whereas the length of the scales shows bradyauxesis 12 . Apart<br />
from weak, individual fluctuations that are of small interest in this<br />
connection, the change in the body-scale relation that occurs before and<br />
after the transformation into the smolt stage is important for us. Accor-<br />
ding to Lindroth, this causes different linear relations for parr and.<br />
adult fish, as far as the anterior radius of the scale is being measured.<br />
L rA<br />
LA c<br />
rc<br />
Adults L<br />
c<br />
length at catch<br />
L<br />
A =<br />
length during.sojourn in the sea to<br />
be determined<br />
rc = radius of scale at catch<br />
r A = radius of scale at length L A<br />
r<br />
s<br />
radius of scale as smolt.<br />
r radius of scale as parr<br />
p<br />
•<br />
[p• 30 3]<br />
The scales of an adult fish can be used forthwith for the cal-<br />
culation of the lengths during the stay in the sea by employing a simple<br />
proportion (equation for adult salmon). For the determination of the size<br />
of smolt L s the value calculated for adult salmon has to be multiplied by<br />
0.85 (equation for smolt). Through inserting the length of smolt Lg and<br />
the measured scale radius r s into the equation for parr one can calculate<br />
every length during the stay in fresh water.<br />
After one has calculated the lengths for Parr for a fish at the<br />
end of the 1st, 2nd, etc. year, one needs to know the natural.griowth<br />
in the river in order to confirm the determination of the age. • 171- 4 erg-<br />
12 Isauxesis, tachyauxesis and bradyauxesis are cases in which the growth<br />
of the part of an organism takes place in part with the same speed, or<br />
faster or slower; in comparison with the entire organism, or with another<br />
part (Huxley, Needham, Lerver 1941, after Lindrôth, 1963a).
•<br />
cr-I<br />
0<br />
4—/<br />
cd<br />
cn<br />
• •<br />
+3 CO<br />
41-1 H<br />
• 0.)<br />
0<br />
r-4.m1<br />
O 4<br />
CH<br />
• +3<br />
■<br />
f•-<br />
O -H<br />
9 a e •-1<br />
a)<br />
e<br />
Q)<br />
0<br />
-P<br />
cd<br />
a)<br />
re%<br />
cd<br />
E-1<br />
co<br />
(p. p.<br />
.fl N: ô<br />
-4r<br />
•<br />
4.1-4<br />
o N... Kb '<br />
1—■<br />
IT I.<br />
ob<br />
N<br />
Lr■<br />
,<br />
4-)<br />
Q 1-1 0'<br />
0 .., 0 .-4 p..<br />
er it s 4 i 4- ,-r<br />
i<br />
.<br />
a<br />
N 9_1<br />
ce<br />
N<br />
en<br />
se;<br />
•i•<br />
N<br />
'e'l•<br />
leb<br />
qs N<br />
....1--<br />
▪<br />
oo •<br />
ou<br />
à<br />
.4. cr. -t- e4 oo -r<br />
.v ..... .<br />
, •<br />
I<br />
coHI<br />
o<br />
,,, *<br />
al w po • -4;, ..n., ,<br />
lea ›. VS' V 0 .11<br />
. ri<br />
• ul<br />
0 g<br />
. 0 MI,<br />
• (1,<br />
c›...%D.,<br />
e--<br />
MD<br />
4 'H n. 44% c4 4/1<br />
...<br />
e<br />
.<br />
o-' cr.'0 IN<br />
,0 0%.„ >à i3;., 7-1 N., el<br />
I ,-r ,,, ,c. I -4- -r<br />
ci■ Ln _p I N VI<br />
+<br />
co<br />
a■<br />
T.".<br />
• a....e<br />
nt scr<br />
t'i<br />
es-<br />
N<br />
H '...<br />
0<br />
oo<br />
i<br />
ni<br />
0,<br />
•1" 4.n<br />
4-4<br />
I •<br />
00 • +3<br />
. Cr,<br />
o..4.4 cU ot 00 oo oo..<br />
... .6 .., rsi .... 4 cr.<br />
r-1<br />
•<br />
• •<br />
r4 ~i<br />
er—cd1 o<br />
.00 eme com m<br />
ca 0 +, p 0 0<br />
•<br />
• :1<br />
.w.w e<br />
a) a) ca 4<br />
A +<br />
-P<br />
e<br />
0 0 H<br />
0' -P c5 (o • §<br />
..-1 › a) El<br />
F-1 -P • H u-■<br />
(1.) 0 CH r4 r-I<br />
P.4 r-i 0<br />
• 0.) • 0 •<br />
CO Cr) (I) C \<br />
O -P X<br />
0 4-i.1-1 u)<br />
P:1 9-1 0 0 0 0 r.<br />
-P4-, •r•I 4-1<br />
r-I • rl O a -P<br />
0 ca 0 • 0<br />
0 0<br />
g 9 `.1<br />
•ri Z A •ri<br />
CJ N%4 LC-NU)<br />
and counts of sclerites have been<br />
— 126-<br />
If the recaciculated.lengthS of parr are, e.g., 5, 11 and 17 Cm, and if<br />
the results agree with the amounts of growth that have been ascertained<br />
otherwise, then this result indicates<br />
a correct . age determination.<br />
Unfortunately,.things are not<br />
quite as simple, since hardly any meas-<br />
urements of lengths in the natural<br />
stock of parr have been carried out.<br />
•All figures for the mean lengths of'<br />
parr that are available have been ob-<br />
tained through recalculation (W. J.<br />
Menzies 1925, G. Alm 1928a, F. Chrzan<br />
1959b). Furthermore, we have here as-<br />
sumed a simple proportionality, so that<br />
changes in the body proportions have<br />
not been taken into account. However,<br />
even these statements .can help us in<br />
making a step ahead. When the analyses<br />
give the same result or a similar one<br />
as the investigations of other authors,<br />
then the possibility of an erroneous<br />
'determination is slight, even when the<br />
recalculation does not result in the<br />
actual length.<br />
In every case recalculations<br />
carried out for the presentage deter-<br />
minations. In addition the entire material has been - determined twice.
5.3. The'age composition of the German catches<br />
- 127-<br />
Age determinations have been carried out in salmon of the<br />
Baltic Sea principally by T. H. ervi (1938, 1948) and G. Alm (1928a, 1934)<br />
and later also by J. Jokiel (1958), M. N. Lishev and E. J. Rimsh (1961).<br />
These, however, concerned,ascending spawning fish. The pelagic stock of<br />
salmon has been investigated by D. Dixon (1931, - 1934) and A. Willer and<br />
W. Quednau (1931), but, to be sure,, only on hand of a very mall amount Of<br />
material. P. Brandtner (1938), who received, among others, material from<br />
Quednau and Bahr (catches from the Danzig Deep), could carry out slightly<br />
more ample analyses. The . results of F. Chrzan (1959b) and of R. Kgndler<br />
and M. Whmann (1957), the work of whom was continued by F. Thurow (1960),<br />
were based on numerous samples of scales. A considerable material has been<br />
worked over recently by . 0. Christensen (1963, 64).<br />
5.3.1. Results of the analyses of January catches.<br />
When the age determinations are to be.evaluated iicyrespeot<br />
the study of the stock of salmon, te questions will be of interest: the<br />
l'ety-dAsses (1)..0bei<br />
strength of the -yea-r-La.-sats and the strength of the sea year classes. From<br />
Table 31 can be seen that the members of a brood year class can reach the<br />
smolt stage after very variable periods of life. A small part of the fish<br />
of a certain year class x emigrates already after one year from the rivers<br />
and thus joins with two-year old emolt of the year class xr1, as well as<br />
with three-year, four-year and five-year olds of the year classes x-2, x-3<br />
and x-4. Salmon of five different year classes form together in general<br />
one sea year class. In the following year smolt of the.year classes x + 1,<br />
x, x-1, x-2 and x-3 unite into a further sea year class. The analyses of<br />
tyabti_ eet, dASSCS<br />
. age..of catches.at sea thus show always that yeerLd-eem as well as sea<br />
year classes are groups of very heterogeneous composition. The sea year<br />
[P. 304]
- 128-<br />
. A<br />
r i" 'MAY etkeiS<br />
classes consist of different--yearta, but they show an extensively<br />
by-boet yetw•-c&sses<br />
uniform growth in the . sea. On the other hand, the yeaele-eete contain fish<br />
of the same age, but of very variable growth. From the point of -view of<br />
C.11, 5% C.<br />
the study of the stock we shall investigate the brood year's-se-43-, because<br />
we are interested in the number of the fish of one population. Wé analyse<br />
the sea year classes on account of the growth.<br />
cLtses<br />
5.3.1.1. The brood year t -s-se4e<br />
In Table 31 the percentage composition of the catches has been<br />
CetekeS<br />
recalculated as the corrected line eaetuxes per unit effort of Table 15<br />
in order to make possible quantitative comparisons. To begin with, it can<br />
-4ew-ekts<br />
be established that a -year-l-s-ae-t can be represented in the catches for a<br />
maximum period of eight years. The first of the fish,to be captured are<br />
those that emigrate from the river already after one year, and that were<br />
thus in the first year of stay in the sea. During the following four •<br />
years are added to these those salmon that lived for two, three, four or<br />
even 5 years in the river. The oldest of all the fish ekamined waenine<br />
years old and belonged in the-age groUp 3.6. The fish thus remain at Most<br />
for six years in the Baltic Sea.<br />
However, the salmon do not enter iMmediately ifter.reeping the<br />
Baltic Sea into the exploited phase. There axe only - very few fish that<br />
are caught already in the first year of their stay in the Baltic Sea.<br />
Their share in the total catch lies in general below one per cent. Only<br />
during the third year after hatching is the caught share in the year%t<br />
cc% more than one per cent and after the seventh year it .1a1ready lies<br />
again below one per cent. In this connection each year- 1-&-e-e4 becomes ef-<br />
fective . only during five fishing periods. However, it plays a decisive role .
-129-<br />
with shares in the catch of over 10 per cent only during three years,<br />
namely in the fourth, fifth and sixth year after hatching. During the<br />
fifth year the share amounts on an average toet0 55 Per cent, whereas the<br />
shares during the fourth and sixth year amount to 17 to 32 Per cent each.<br />
If flow from one year to the next a new group of salmon of the<br />
flame agé enters the exploited phase of the brood ear- eet-, then the<br />
entire composition of the catch changes with the average age of the smolt.<br />
e.■,v - elk 'IS el<br />
One can therefore not inôlude the fish of the different ycar's mete that<br />
appear during a fishing season in a quantitative- comparison. That follows'<br />
yeee-e-Lts e-C<br />
from the average smolt age of the individual brood yeer4-ee4e in subse-<br />
quent fishing periods (Table 32). It is seen that in the very important<br />
fourth, fifth and sixth years of life the smolt age increases on an average<br />
by 0.9, 0.6 and 0.6 years. In an investigation of the strength and of the<br />
yeey -clAsses<br />
smolt age of different brood jeari se-tie., only the entire span of life Or<br />
a comparable section of life that should be as large as possible can be<br />
used.<br />
L. bsterdahl (1963). has analysed the stock of salmon in the<br />
[P. 30 5]<br />
:yew-<br />
Bicklean. He found that the determination of the mean smolt age of a yetela<br />
— el Ls<br />
-ales.<br />
„e<br />
with the aid or the scales of adult fish is subject to errors, because<br />
the mortality of the smolt is dependent on size. The recapture of fish that .<br />
had been tagged as smolt was the higher the longer the fish were at the<br />
time of tagging. B. Carlin (1963) arrived at the saine result on hand of<br />
numerous taggings. 8sterdahl concludes from this that the counting of scale<br />
rings gives a smolt age that is too high On an average. The results indicate,<br />
however, that the error is not very large. In addition, a mort•ity that<br />
may possibly be affected by the tagging has not been taken into account.<br />
■■■■<br />
71e,
•<br />
- 130 -<br />
The conclusions that have been drawn from Table 32, will remain<br />
unchanged in any case even if the mortality is dependent on size. Because<br />
the smaller fish fall prey to predators only during the first monthS, all<br />
values would be slightly lower. For the saine reason it is possible to com-<br />
pare the mean smolt age of all fish in different fishing seasons with one<br />
another. It is found that the fluctuation are very small and amount at<br />
most to 0.25 years. The lowest smolt age could be established as 2.54 and<br />
2.51 years, respectively, in January195 8 and April 1963. It was . highest<br />
with 2.78 years in January 1962 (Table 31).<br />
yeee - cLue s<br />
It might now be attempted to compare the brood y---set. with .<br />
one another in regard to their average smolt age (Table 31). Since age<br />
-yet.e-eieLes<br />
*analyses for the entire life in the sea are available only for the year l o<br />
of 1955, a period of that length cannot be used as the basis for a<br />
yew-eLss<br />
comparison. It is true that this is not necessary, because a brood year's<br />
ite4..plays : a role for the catch only during five years and is of importance<br />
even for three years only. More than 90 per cent of the tetal-yields from<br />
yea. - 'J<br />
a yeeeLs-set are obtained during this period.<br />
yeev - S<br />
Let us consider first the year's-meta that can be followed com-<br />
'yeee -akcs<br />
paratively for five years, namely 1955 and 1956, and then the yearle-sete<br />
yege-dA.s.r<br />
1954 to 1957 that can be compared> for three years. For the yearts-set.<br />
1955 is found an average smolt age of 2.36, 2.41 and 2.42 years, when 3,<br />
5, or 6 years, respectively, are used as basis. On the other hand, the<br />
etét.ee •<br />
yesei-e-sett 1956 shows a smolt age of 2.93 or 2.82 years, respectively,<br />
when 3 or 5 years of life are taken into account. Thus, the values change,<br />
because the fish with a smolt age of one and five years are not taken care<br />
of sufficiently in the composition that is obtained during the fourth to<br />
'sixth years of life. The deviation, however, is not large so that wescan
"ervoct.<br />
Yeer-Le-<br />
-e-t.<br />
'4.y-c.1*.e.,s<br />
2nd 3rd 4th 5th 6th 7th 8th 9th<br />
7 131 -<br />
compare the four year's sets 1954 to 1957 on the basis of three fishing<br />
periods. According to this, the smolt age was 2.7, 2.4, 2.9 and 2.8 years.<br />
That are rather . considerable deviatiensamditds questionable whether such<br />
fluctuations, when the share of every river remains the. same, can be at-<br />
tributed to changes in all rivers, or whether they are to be attributed -<br />
to changing shares of thé rivers.<br />
[p. 308]<br />
It has already been shown (4.1.2.) that the salmon of the nor-<br />
thern Gulf of Bothnia show the tendency to migrate later and not as far<br />
to the south than fish from more southerly rivers. In this connection we may<br />
• yefee7cLues<br />
Table 32. Mean smolt age of different j.earLs-gete in the sea<br />
in consecutive years.<br />
1950<br />
1951<br />
1952<br />
1953<br />
1954 •<br />
1955<br />
1956 .<br />
1957<br />
1958<br />
1959<br />
1960<br />
1,0<br />
1,0<br />
1,1<br />
• 1,1<br />
1,1<br />
1,0<br />
1,0<br />
1,0<br />
,<br />
1,9<br />
1,9<br />
1,8<br />
1,9<br />
1,9<br />
1,9<br />
2,6<br />
2,8<br />
2,6<br />
2,9<br />
2,9<br />
2,7<br />
3,1<br />
3,4<br />
3,2<br />
3,4<br />
3,7<br />
3,3<br />
3,4<br />
4,1<br />
3,8<br />
4,0<br />
4,6<br />
3,6<br />
3,8<br />
5,0<br />
3,7<br />
3,0<br />
3,5<br />
3,4<br />
3,0<br />
.<br />
.<br />
• -<br />
Me an<br />
smolt age 1,0 . 1,05- 1,88 2,75 3,34 3,92 3,73 3,0<br />
Difference 0,05 0,83 0,87 0,60 0,57<br />
make a comparison with the figures for smolt ages by G. Alm (1928a).<br />
Rivers north of 65 ° N . had an average smolt age of 3.15 years in 1915 to<br />
1944. The corresponding value for rivers between 61 ° and 64 ° N was 2.54<br />
years.and in the lerrum, 56 ° N (1919 to 32) it was even 2.03 years 1 3.<br />
13 It is possible that the actUal smolt age has been lower - in all regions,<br />
on account 6f the mortality dependent on size; however, the values remain<br />
comparable with one another and aléo . with the data presented here.
Table 3.1. Composition of the German salmon catches by brood year's sets, January 1958-62,<br />
as number of salmon per 100,000 - hooks according to the line catches per unit effort<br />
of Table 13.<br />
Brood Years in Year of investigatibn Composition<br />
year's .fresh 4th - 6th year 3rd - 7th year<br />
set water 1958 1959 1960 1961 1962 1962' Iiiee -Nùàber Smolt p .ç . Number Smolt<br />
Etee age •<br />
3 3<br />
1950 4 1<br />
5 2<br />
2 5<br />
1951 3 20 .<br />
.<br />
4<br />
5 -<br />
17<br />
4_ 7<br />
.<br />
2 34 1<br />
1952 3 150 20 2 1<br />
4 47 31 1<br />
,5 29 2<br />
1 - 6 1 (4)<br />
2 214 31 - 2 (27)<br />
1953 3 299 270 9 1 (48) (1380) (2,86)<br />
4 272 54 (21)<br />
' 5 4<br />
1 26 11 1 2,8<br />
V<br />
2 195 171- 10<br />
2 27,4<br />
1954 3 747 163 5 66,3 1372 2,71<br />
4 2 45 19 • 3,4<br />
5 1 6 2 0,1
1955<br />
1<br />
2<br />
3<br />
4<br />
23<br />
3<br />
61<br />
506<br />
7<br />
3<br />
135<br />
211<br />
2<br />
5<br />
105<br />
68<br />
2<br />
3<br />
2<br />
'<br />
5<br />
'<br />
5,8<br />
58,6<br />
29,3<br />
6,3<br />
1103 2,36<br />
7,6<br />
55,6<br />
27,7<br />
6,0<br />
1172 2,41 *<br />
5 36 3,1<br />
1 67 40 1 3,9 9,4<br />
2 11 123 79 3 • 2 19,6 19,0<br />
1956 3 . 530 62 6 56,6- 1048 2,93 52,2 1146 2,82<br />
4<br />
.<br />
210 • 10 20,0 19,2<br />
• 5<br />
2 0,2<br />
1 7 28 30 1 2,7<br />
2 2 201 49 • 2 21,8<br />
1957 3 742 79 71,0 1156 2,77<br />
4 • 52 4,5<br />
1<br />
1958 2<br />
3<br />
1<br />
1959 2<br />
3<br />
1960 1<br />
28 30 .2<br />
1 368 80<br />
246<br />
69 , 18<br />
261<br />
1<br />
1 55 146 74 59 101 55<br />
Average 2 451 719 273 286 425 345<br />
0 3 472 1044 385 642 806 337<br />
4 65 305 102 87 210 62<br />
5 6 36 7 6 38 • 2<br />
Total 1049 •2250 • 841 1080 1580 801<br />
Mean smolt. 2,54<br />
2,72 2,64 2,72 2,78<br />
...<br />
2,51<br />
age<br />
34<br />
(890)<br />
6,5 490<br />
32,9 2499<br />
48,5 3686<br />
10,9 831<br />
1,2 95<br />
1 Analysis of catch of November 1962, cf. Table 40 and the conclusion of Chapter 5.5.3.<br />
7601<br />
2,68
- 134--<br />
Within one and the same river the figures vary in the different periods<br />
by a maximum of 0.35 years.<br />
The mean emolt age of the salmon examined from 195 8 to 19 6 3<br />
was 2.68 years. According to the statements of Alm for the Gulf of Bothnia<br />
the salmon of the southern Baltic Sea are being recruited to about only<br />
one-quarter from the rivers of the Bottenwiek, whereas most of the fish<br />
come from the rivers of the Bottensee. The Swedish restocking measures<br />
undoubtedly have lowered the present-day mean gmolt age slightly, because<br />
the artificially reared salmon are being released already at the age of.<br />
two years. Most of these fish have been released in the rivers of the Bot-<br />
tensee, so that the above statement remains valid. This:result agrees with the<br />
figures of Table 22.<br />
Let us return once more to the individual statements. The Yer-t-B ee-<br />
desses<br />
-sets 1955 and 1956 show a smolt age of 2.4 and 2.9 years, with a difference<br />
of 0.5 years. This considerable difference has been caused by the fact<br />
that in one case more than 55 per cent of the fish examined did emigrate<br />
as two-year old smolt, whereas in the other case they did not even amount<br />
to 20 per cent. It has already been indicated that two causes may be res-<br />
ponsible for Ëuoli changes. If only fish from the Bottensee and no salmon<br />
from the northernmost rivers occur in the southern Baltic Sea, then the<br />
.average smolt age of a lilalet-e—ae -el"s t could drop to 2.54 years. This effect<br />
can, however, also be caused by tne salmon emigrating from the rivers on<br />
• an average at an earlier date than in other years. Finally, the influence<br />
• [P. 309]<br />
can have been caused by the living conditions being more favourable after<br />
the emigration in one year than in others so that a higher perdentage of<br />
the younger fish managed.to survive.<br />
Sirice the absence of the northern salmon does not suffice for
- 135 -<br />
yeAy-ctt4<br />
thé explanation for the low smolt age that is shown by the yèeele-eet of<br />
1955, we have to suppose that the main cause.was that the smolt emigrated<br />
earlier. If we assume as before that the share of the northern salmon (be-<br />
eiond 65 °N) was 25 per cent and if we assume further that they emigrated<br />
0.3 years earlier, we obtain with the•aid of Alm's (1928a) average values<br />
for 1915-1944:<br />
Smolt age north of 65 ° N 1 3.15 years - 0.3 years = 2.85 years<br />
Smolt age 61° - 64 °N 1 2.54 years - 0.3 years = 2.24 years,<br />
total average weighted smolt age 4 2.39 years.<br />
s{Cee — elitSSGS ,<br />
Let us now make a comparison of the strengths of the yeealls<br />
'Pe t . In order to include as many of them as possible, we shall again use<br />
as basis the figures for the fourth to sixths years of life. It has already<br />
been pointed out earlier (F. Thurow 1960) that the ye;45.2e4 of 1953 was<br />
very rich in individuals. Only fish in their fifth and sixth year of life .<br />
have been used in Table 31. Nevertheless, we shall•attempt to include them<br />
- cUss<br />
in the comparison as well as the fish of the yeel-e-eet of 1958. With the<br />
aid of Table 31 we can state that on an average 26 per cent of the total<br />
number of the fish in their fourth year of life are caught and an average<br />
of 18p cent of ihe total nUmber are caught in their sixth year of life..<br />
yew- s 5 •<br />
In order not to overvalue in the comparison the yéar's set of 1953, we f-<br />
shall assume that the share in the fàurth year of life is only 16 per cent.<br />
yet.y--chas .<br />
Wé shall apply to the yearlo pet of 1958 the intentionally reduced percenr.<br />
tage of only 15 per cent for the sixth year of life. Thus are obtained the<br />
sie&Y- tb,ts<br />
comparable figures for the six yintr-1-a--ee4a. from 1953 to 1958 in Tkble 31.<br />
yeey: eha se<br />
According to this, the yéeel7e-aete 1953 and 1954, with their high yields<br />
of almost 14 ealmon.Per 1000 hooks stand far aboVe the group 1955 to 1957,<br />
which is in coniparison rather uniform (about 11 salmon Per 1000 hooks).<br />
'
- 136 -<br />
rw-d4ss<br />
The -yeamla-ael of 1958, which yielded about nine salmon per 1000 hooks,<br />
must probably be designated as weak. Even an increase of its share in the<br />
sixth year of life to 20 per cent results only in a number of 9.5 salmon<br />
per 1000 hooks.<br />
In conclusion let us follow up how the appearance of the ill,-<br />
yeer-Ciat.e<br />
dividual ye-axle-es-to affected the yields of the various fishing periods.<br />
dAse:k<br />
Whereas every yeeele-the't contributes the highest amount to the catches<br />
mostly during the course of the fifth year of life, the salmon that had<br />
hatched in 1955 aPPeared already in the fourth year of life ', that is,<br />
during 1958/59 in the largest number of individuals. At the same time the<br />
dess<br />
good yeau'iy, bet, of 1954 reached in the fifth year of life the maximum of<br />
crebel,e.s.<br />
exploitation. In this way the very good captures-per unit effort of 22.5<br />
Salmon per 1000 hooks were realized.<br />
Since the fish that had hatched in 1955 had passed the peak. of<br />
exploitation already in 1958/59, that is a year earlier than normal, a<br />
group of similar strength was missing from the catches Of the season 1959/<br />
1960. Thus the Oc4ere per unit effort dropped to 8.41 fish per 1000 hooks.<br />
A case similar to that of 195 8/59 occurred during the season 1961/62, when<br />
desses .. •<br />
the two reerks-eets 1957 and 1958 experienced the peak of exploitation,<br />
cettk<br />
which resulted in an average ese44.14e of 15.8 salmon per unit effort. Con-<br />
sequently such a maximum was missing again in the following season 1962/63,<br />
Cabc-iL<br />
in which a oaptuxe-per unit effort of only 8.0.salmon was reached.<br />
. In summary, the above detailed statements show clearly that the<br />
yeev.- . cless .<br />
strength of the brood ytar'o set is of decisive importance for the yields<br />
of the fishery on thé high seas. The annual fluctuations in the catch can<br />
f.urthermore be influenced by the different age of the smolt of the<br />
• thisç es. .<br />
SeertM4 The yter-i-e-sems 1953 and 1954 must be designated as strong, 1955 to<br />
1957 as medium strong and the yle, of 1958 must Probably be deeignated<br />
et4;-Ls -
• •<br />
_<br />
Table 33. The composition of the German salmon catches by age groups, January 1957-6 2/<br />
Navember 1962. •<br />
Age 19571 1958 1959 - 1960 . • 1961 1962 19621 Total<br />
igTOUP<br />
A.B N. p.c. Num. p.c. Num. p.c. Num. . p.c. Num. p.c. Num. p.c. Num. p.c. Num. p.c.<br />
■111.11•1•■••■11.■••■<br />
1.0+ 2<br />
2.0+ 4 3 1<br />
3.0 + 4 0,3 2 9 1,2 7 0,5 1 0,1 '2 2 0,2 23 0,3<br />
4.0+ 1 2<br />
• 5.0 + 1 . •<br />
1.1 + 30 23 44 35 48 42<br />
2.1 + 249 174 193 248 252 325<br />
3.1 + 673 77,2 381 725 54,2 257 558 72,0 331 646 49,1 651 1026 77,2 509 979 90,5 306 741 74,3 5348 69,3<br />
4.1 + 60 94 71 84 144 65 -<br />
5.1 + ' ' 5 7 8 26 3<br />
1.2 + 34 21 63 37 21 22<br />
2.2 + 273 59 212 97 33 99<br />
3.2 + 186 21,3 191 521 39,0 93 186 24,0 256 618 46,9 129 286 21,5 42 96 8,9 99 233 23,4 2126 27;6<br />
4.2+ ' 21 11 84 23 12<br />
5.2+ 2 2 3 1<br />
1.3+ 8 4 5 1 3<br />
2.3 . + 43 11 16 6<br />
.<br />
2 2<br />
3.3 + 13 1,5 25 77 5,7 7 22 2;8 15 37 2,8 7 14 1,0 1 3 0,3 8 14 1,4 180 2,3<br />
4.3+ 1 1 1<br />
1.4+ 1 1 .<br />
2.4+ 7 11 0,8 4 7 0,5 1 0,1 2 2 0,2 2 7 0,7 28 0,4 .<br />
3.4+ 4 2 1<br />
1.5+ 1 1<br />
2.5 + - 1 2 0,2 1 0,1 1 2 0,1 5 0,1<br />
3.5+ , 1<br />
Total ; 1172 100,0 1338 100,0 775 100,0 1317 100,0 1329 100,0 1082 100,0 997 100,0 7710 100,0 ;<br />
1 cf. Talle 40 and conclusion of Chapter 5.3.3.
as weak.<br />
5.3.1.2. The sea year classes<br />
- 138 -<br />
As we have seen, all the fish that have hatched from the eggs<br />
in the same spring form, in regard to Age, a uniform group, the brood<br />
ysey-dass<br />
ycarts eet. In contrast, the individuals in the sea year classes are those<br />
fish that have transformed into smolt in the same spring and that have<br />
left together the rivers and entered the Baltic Sea. Consequently, one<br />
le6w- Cieeses<br />
can talk<br />
Ye4rof<br />
ycaetc cot,: also in regard to these fish, namely of --yeee 1s<br />
c(4.ss4-s<br />
-<br />
-sate of smolt, which are, however, of very heterogeneous composition in<br />
regard to their actual age.<br />
Let us now follow up the exploiteà sea year classes on ihand of<br />
Table 33. During the - first year in the Baltic Sea (A.+) the .salmén are<br />
practically not caught. On an average the share of the sea year class A.+<br />
[P . 511]<br />
in the catches amounted to only 0.3 per cent during the years 1957 to 1963.-<br />
These fish are hardly ever caught in the nets, because they can slip<br />
through the meshes. It is, however, astonishing that even with small<br />
hooks only very few fish of the age group A.+ have - been captured. We can • .<br />
theref ore assume ihat these amall salmon either live in a region.that ia<br />
different from that of the large fish, or that they do not take the bait.<br />
The latter would mean that they use a different basic food than the older<br />
fish. It has already been established (2.2.3.2.) that the salmon can tiver-<br />
come the sprat used as.bait only after they have reached a length of about<br />
[13. 312]<br />
27 cm. According to Lindroth (1961b) they liVe before that mainly on<br />
flying insects.<br />
It iatheamfore probable that the young salmon live in shallower<br />
waters until near the end of their first year in the sea, where they can
Table 34. Composition by age of catches of salmon<br />
according to various authors as percentage of the<br />
numbers, line catches.<br />
Season Author Sea year classes<br />
A.+ A.1+ A.2+ A.3+ A.4+ A.5+<br />
. .<br />
1945/46 OutzAN 36,4 59,8 9,8<br />
1946147 CHRZAN 16,0 57,0 21,0 6,0<br />
•<br />
; 1947/48 CHRZAN 2,7 41,0 51,8 4,5<br />
1948/49 CintzAH 37,5 38,1 18,8 5,6<br />
1949/50 CHRZAN 7,9 81,6 9,8 0,6 .<br />
1950/51 CHRZAN 9,2 72,3 18.,5<br />
' 1951/52 .CletzAN ' . ••10,8 64,6 22,6 2,0<br />
1952/53 CHRZAN 17,3 66,0 15,8 0,9<br />
1953/54 Clutz.AN 3,5 55,1 36,9 4,0 0,5<br />
1954/55 CHRZAN 0,2 51,3 44,4 4,0 0,1<br />
1954/55 ICINDLER/LCIHMANN 37 58 5<br />
1957/58 CHRISTENSEN 72,9 25,3.<br />
1958/59 CHRISTENSEN • 83,0 16,0<br />
1959/60 CHRISTENSEN 65,4 , 29,6 •<br />
1960/61 .CHRIS'TENSEN 79,8 18,7<br />
1961/62 CHRISTENSEN 83,5 15,6<br />
1962163 CHRISTENSEN 76,8 20,9<br />
1963/64 CHRISTENSEN 0,1 71,3 27,1<br />
. 1957/58 THUROW 0,3 . 54,2 39,0 5,7 0,8<br />
1958/59 THultow 1,2 72,0 24,0 2,8 • •<br />
1959/60 THUROW 0,5 49,1 46,9 2,8 0,5 0,2<br />
1960/61 THUROW 0,1 77,2 21,5 - 1,0 0,1 0,1<br />
1961/62 .THUROW 90,5 89 0,3 0,2 0,1<br />
1962/63 THUROW 0,2 74,3 23,4 1,4 0,7<br />
1928-36 DIXON 24 60 15 - 1<br />
1945-53 CHRZAN . 16,5 60,1 21,0 2,4 i<br />
1953-55 CHRZAN 1,8 53,2 40,7 4,0 0,3<br />
1957-63 l'HuRow 0,3 68,4 28,4 2,4 0,4 0,1 1<br />
• 1957-64 CHRISTENSEN 76,1 21,9 i<br />
. _. .<br />
- 139 -<br />
also capture small food animals on the bottom; they are joining the larger<br />
animais only gradually. This behaviour surely is the cause of the fact that I<br />
it was formarly possible to capture considerable amounts of "speizken" (sal-,<br />
9<br />
mon in the first' year in the sea) at the coast of Pomerania).<br />
The largest share in the catches is provided by the sea year<br />
class A.1+, which amounts to an average of 69.3 per cent. During their<br />
second year in the sea, obviously all salmon are in the exploited phase.<br />
The same is to be expected for the fish of three winters (A.2+), which ac-<br />
count for 27 ..6 per cent of the yield on an average. The percentages ate<br />
very small'of.thè following sea year classes: A.5+ with 0.1 per cent,14+<br />
with 0.4 per cent and A.5 with 0.1 per cent. Among the about 7000 fiàh
- 140<br />
-<br />
that have been analysed there was not a single salmon that had lived in<br />
the Baltic Sea for more than six years. The fishery rests thus principally<br />
on the two sea year classes A.1+ and A.2+, which account on an average for<br />
almost 97 per cent of the yield.<br />
If we cômpare these results with the statements by other authors<br />
(Talle 34), we find that the sea year class A.2+ was exploited the heaviest<br />
until the season of 1952/53, when it brought about 60 per cent of the yields.<br />
The classes A.1+ and A.3+ accounted together for a further 38 per cent.<br />
The picture changed considerable during the subsequent years, so that the<br />
sea year class A.3+ played practically no longer a substantial role, while<br />
the main share shifted from the fish of three winters (A.2+) to those of<br />
two winters.(A.1+).<br />
It must be obvious that the analyses of captures until 1953 •<br />
cannot have given a true picture of the conditions of the stock. Under<br />
average 'conditions the sea year-class A.+ must have the highest number of<br />
individuals in the stock, whereas the number of fish in the following sea<br />
year classes diminishes steadily through fishing and natural waste and<br />
the emigration to the spawning grounds. A. fishery that is exploiting the<br />
stock representatiVely, must also reflect these relations.<br />
Although F. Çhrzan (1959b) has examined-only an average of<br />
160 salmon, a possible error may have been compensated through the for-<br />
[1:4 313]<br />
mation of mean values. He hils established that the changes in the compos-<br />
ition of the catches around 1953 are connected with the use of smaller<br />
fishing hooks. The Polish fishermen changed during this time from hooks<br />
-with an opening of 25 mm to those with an opening of 13.5 and 15 mm.:Since<br />
• at that time.the bait-for the large hooks consisted of herring, it is'pos-<br />
sible that significant differences occurred between the catches with the'
- 141 -<br />
yeAy-cle..es<br />
Table 35. The strength of the ye-are-Es-seta of smolt as number<br />
of salmon per 100,000 hooks according to the line captures<br />
per unit effort of Table 15.<br />
■•■•■■<br />
Number Evaluation<br />
Year's in 2nd Eval- figure re-<br />
A.+ A.1+ A.2+ A.3+ A.4+ À.5+ a. 3rd- uation calculated<br />
set year figure after Kând-<br />
é.;“ott ler 19 64<br />
"Wy)<br />
.<br />
1953 8 .<br />
•<br />
1954 •<br />
• . • 61 ' 2<br />
• 1955<br />
195,6 '<br />
- 409 '62 .<br />
568 . ' 540 • . 23<br />
5 • 1<br />
1 - 4<br />
(1683) 1<br />
1108<br />
(17)<br />
11<br />
1957 3<br />
1958 • 27<br />
1959 6<br />
1621<br />
411 .<br />
833<br />
394<br />
233<br />
143<br />
- 11"<br />
5<br />
11<br />
3 -<br />
6<br />
2015<br />
644<br />
976 -<br />
20<br />
6<br />
i0<br />
12<br />
8<br />
11<br />
,<br />
• 1960<br />
1961<br />
1962<br />
1<br />
2<br />
1425<br />
593 :,<br />
187<br />
•.<br />
•<br />
-<br />
1612<br />
(803)1<br />
16<br />
• • (8)<br />
17<br />
13 .<br />
.<br />
.<br />
0 7 909 318 29 4 1 1225 12<br />
1 •Figures completed through estimates.<br />
[0 = average]<br />
hooks of 15 and 25 mm openings. Chrzan also mentions that the enforced<br />
cowseyve,t,,m,<br />
Hprefferieft4i-ea during the war had thé consequence that there was a larger<br />
share of older fish than before and afterwards. • leaf — ciesses<br />
Let us flow attempt to compare the individual yettele-eebs of<br />
smolt with one another in regard to their strength. With the aid of the<br />
entries in Table 33 and the line •keeee per unit effort in Table 15 com-<br />
parable values have been assembled. ih,Table 35. For an entirely exact com-<br />
Yee-r-ct,ts<br />
parison each ye.selle-se4 would have. tp te taken into account from its first<br />
appearance in the exploited phase until its:disappearance. Since the sea<br />
ye e<br />
year classes A.1+ and A.2+ of every yeer-I-e-set of gmolt supply on an aver-<br />
age more than 95 per cent of the yields, we can use for the compai.ison<br />
also the figures for these two classes. With the aid of the mean numerical<br />
.ratio of A.1+ to A.2+ for 1956-1960 one can in addition estimate the prob-<br />
able total number of the individuals for the capture per unit effort for
déro:<br />
the yeetri-s-zre4s. of 1955 and 19 6 1 (figures in parantheses).<br />
- 142 -<br />
The manner of presentation in Table 35 has the advantage that<br />
it is not necessary to employ the very relative expressions "good" or<br />
"bad". The number of- individuals of the . sea year classes A.1+ and A.2+<br />
that were caught per 1000 hooks provides an absolute comparative possibility.<br />
According to the present results one can consider as average<br />
ww-644see .<br />
those that have an evaluation figure of 10 to 14 (10 to 14<br />
salmon per 1000 hooks a:1day in the sea year classes A.1+ and A.2+). It •<br />
v - eLss<br />
can therefore be dèduced from Table 35 that.the yeler'r-eet-e.of smolt /e<br />
1955, 1957 and 1960 with evaluation figures of 17 to 20 can be called good,<br />
those of 1956 and 1959 (evaluation figures 10 to 11) cari be called average,<br />
and those of 195 8 and 1 9 61 (evaluation figUres.6 to 7) can be called poor.<br />
R. Kandler (1964) has used the average yield of a cruise in<br />
M.S.<br />
order to be able to evaluate the strength of the year-Le-sat. The age*com-<br />
position had been obtained with the aid of weight statistics (cf. 5.3.3.).<br />
According tO this, salmon under 5 kg belong into the sea year class A.2<br />
and fish over 5 kg belông into the sea year class A.3. On account of the<br />
unknown number 'of older fish and of sea trout, as well as on acbount of<br />
the fluctuations in growth, he had to apply annually a correction to the<br />
yields of the cruises. }lis results have been recalculated as evaluation<br />
figures and inserted in Table 35. The two investigations show approximately<br />
yedui7eAses<br />
similar results for the **ele--e -: ;.:e-t& of gmolt for 1959 and 1956. However,<br />
yem, eid4g-see<br />
there are considerable differencesl'or the yeaxle- ete Of 1957, 1958 and<br />
1961. It had already been pointed out hy way of introduction (cf. 2.3.3.1.)<br />
that the number of cruises during a longer period does not constitute a<br />
good measurement for the fishing effort, because the eitmtbe.r of gear per<br />
cutter has risen steadily. This.has also considerably impaired the
- 143 -<br />
•<br />
U7,) tdL<br />
comparablenece of the yields of cruises that had been selected as eapteee<br />
per unit effort.<br />
Let us examine once more the age composition of the Catches in<br />
Table 33 in order to discover the cause of the fluctuations in the catches<br />
yelw-at,s<br />
of the sea year classes A.1+ and Ae2+. In 1958 the average yeeke-la-eet of<br />
• yewgmolt<br />
of 1955 as A.1+ contrasts with the good y arls-set of smolt of 1955<br />
as A.2+. For this reason the share of the sea year class A.1+ WaA onky 54 per<br />
cent. A year later appear together the good yeaele act of smolt of 1957<br />
as A.1+ and the average of 1956 as A.2+. A.1+ accounts therefore for 72<br />
per cent of the catches. In 1960 the sea year class A.1+ is represented<br />
ye,v-éless yeew-<br />
by the poor yearic-cet of smolt of 1958. In comparison with the good yecela<br />
CA.45<br />
Set of 1957 (A.2+) it yields a share of only 49 per cent. In 1961 the av-<br />
erage ycartc7 act of smolt of 1959 as A.1+ in comparison with the poor one<br />
of the year 1958 made up 77 per cent of the catches. In the yeax 1962 the<br />
[P. 314]<br />
good yearls-cet of smolt of 1960 furnished even 90 per cent of the catches,<br />
de,ss<br />
whereas the sea year class A.2+ is represented by the average yeario sot<br />
of 1959. The percentage of the sea year classes in the catches is thus<br />
y eev<br />
alwgys dependent on the relative strength of the yecTlezzeefs of smolt.<br />
5.3.1.3. The salmon with spawning marks<br />
During their spawning migration, the salmon probablycease to<br />
feed already before they enter the rivers. It has, already been stated that<br />
the development of the gonads is accelerated during this period. Since the<br />
fish also have to supply the energy for the spawning migration and for the<br />
spawning, all body reserves are being mobilized. Among other things, there<br />
is a degradation of Substance on the scales (T. H. Jgxvi and W. J. M.<br />
Menzies 1936): This involves a more or less complete resorption along the
- 144' 7<br />
margin (Fig. 33). In those fish that survive the migration and that manage<br />
to return to the sea, this resorption zone is usually plainly visible. It<br />
is called the spawning mark.<br />
Fig. 33. Scale of salmon with spawning<br />
mark, 91 cm, 2.2G1. (After B. Carlin.)<br />
The ntimber of fish with spawning marks that were found during<br />
age determinations has occasionally been employed for the evaluation of<br />
the composition ofe the stock in order to denote the waste. In Table 36<br />
have been assembled the data of F. Chrzan (1956b) and of R. K4ndler . and<br />
M. Liihmann (1957) together with the present data.<br />
F. Chrzan found during the season 1947/48 a very high value of<br />
11.2 Per cent. The figure can perhaps be considered to be accidental, be-<br />
cause in this period a total of only 260, mostly large, salmon were ex-<br />
amined. For the rest, the fluctuations are rather small. G. Alm (1934)<br />
already -found in the catches in the Baltic Sea a figure of 3.2 per cent.<br />
F. Chrzan (1959b) ascertained an average value (1945-1955) of 3.7 per cent,
•<br />
whereas the present data .(1957 to 1963) give 2.A per cent.<br />
- 145 -<br />
R. Kgndler and M. Lehman (1957) have already pointed out that<br />
the share of the salmon with spawning marks 1epends on the age composition<br />
of the sample of catch examined. The older the salmon are that have been<br />
caught, the more specimens with spawning marks will be found among them.<br />
This furnishes also the partial explanation for the fluctuations of the<br />
values in Table 36, when one compares them with the composition in age.<br />
Furthermore, it becomes also clear why G. Alm (1934) and T. H. and (1938)<br />
[P. .315]<br />
found the high percentages of 7.5 and 6.3 per cent, respectively, of salmon<br />
who were spawning again. The percentage of fish with spawning marks in the<br />
total catch thus gives hardly any information other than that obtained<br />
anyway through age determinations. On the other hand, one can answer other,<br />
important, questions:<br />
(1) At which age do salmon migrate to spawn?<br />
(2) How grèat is the percentage of fish with spawning marks in the indiv-<br />
idual age groups?<br />
(3) What percentage of the utilized stock migrate to spawn?<br />
In Table 37 the fish with spawning marks have been divided ac-<br />
cording to time of'spawning and the age at spawning. - The number of fish<br />
that did sPawn in 1962 could not not be taken into account completely,<br />
[p. 316]<br />
because all survivors had not yet returned by the time of the last examin-<br />
ation (spring of 1963); On the other hand, the number of the older fish had<br />
already been reduced through mortality. If we compare the total result with<br />
the age compositions for the years 1957 to 1961 that have been investigated<br />
best, .there is found no substantial difference. About 50 per cent of all<br />
fish on spawning migration consisted of fish that were in the third<br />
•
•<br />
Table 36. Percentage of salmon with spawning marks in the<br />
Baltic Sea.<br />
Author<br />
CHRZAN<br />
CHRZAN<br />
CHRZAN<br />
CHRZAN<br />
CHRZ AN<br />
CHRZAN<br />
CHRZAN<br />
CHRZ AN<br />
CHRZAN<br />
CHRZAN<br />
K.ÂNDLER/LüHNIANN<br />
THUROW<br />
THUROV<br />
!THUROW<br />
• THUROW<br />
THUROW<br />
THUROW<br />
1945/46<br />
1946/47<br />
1947/48<br />
1948/49<br />
1949/50<br />
1950/51<br />
1951/52<br />
1952/53<br />
1953/54<br />
1954/55<br />
1953-55<br />
1957/58<br />
1958/59<br />
1959/60<br />
1960/61<br />
1961/62<br />
1962/63<br />
2,3<br />
4,0<br />
11,2<br />
3,6<br />
2,5<br />
4,3<br />
3,1<br />
2,6<br />
2,0<br />
1,0<br />
2<br />
3,3<br />
4,3<br />
3,3<br />
1,0<br />
0,7<br />
1,9<br />
30<br />
16<br />
3<br />
38<br />
8<br />
9<br />
11<br />
17<br />
55<br />
51<br />
54<br />
72<br />
49<br />
77<br />
91<br />
66<br />
- 146 -<br />
Salmon with Share of sea<br />
Season spawning marks yeax class<br />
in per cent A.1+ in total<br />
catch in p.c.<br />
Table 37. Time of spawning and age at spawning of fish<br />
with spawning marks that were caught in 1957 to 1963, as<br />
number of salmon per 100,000 hooks (percentages in<br />
parantheses), 162 salmon examined.<br />
Time<br />
of<br />
Age at spawning<br />
spawning A.+ A.1+ A.2+ 4.3+ A.A+ A.5+ Total<br />
.<br />
1954 1 1<br />
1955 1 '1 ' 2<br />
1956 9 . 13 5 27<br />
1957 3 14 25 7 1 50<br />
1958 8 38 20 66<br />
1959 1 6 8 7 2 1 25<br />
1960 3 3, 2 1 9<br />
1961 1 6 7 14<br />
1962 1 1<br />
Summe gcsamt 4 (2) 43 (22) 95 (49) 46 (23) 5 (3) 2 (1) 195<br />
Summc 1957 61 4 (2) 32 (20) 80 (49) 41 (25) 5 (3) 2 (1) 164<br />
Summe gesamt - total sum, Summe = suml<br />
younger age group 4.1+ (grilse) and 25 per cent constituted the next older .<br />
age group A.34.
Sin%<br />
0,1 2,8 37,0 96,8 100,0<br />
- 147-<br />
If we compare these results with the series - of Swedish measure-<br />
ments of lengths in ascending salmon (Fig. 22),'we find that the bulk of<br />
the ascending fish here also is formed • y the sea year class A.2+. The<br />
fish that migrated already in their second year in the sea (A.1+) are<br />
grilse. Of the older groups, the sea year class A.2+ on the one hand and<br />
the classes A.3+ to A.5+ on the'other form each a maximum in the frequency<br />
distribution of the Swedish series of length measurements (3.2.3.).<br />
If one collects together correspondingly the age groups of the<br />
Table 37 and neglectF the grilse, then the sea.year class A.2+ constitutes<br />
a share of 64 per cent. F. Chrzan (1959) found on an average during the<br />
years 1945 to 1955 the share of the sea year class A.3+ to be more than<br />
60 per cent.<br />
Table 38. The share of the salmon with spawning marks in<br />
the sea year clsses.<br />
Year of Age groups<br />
-<br />
invest- A.1+ A.2+ A. 3+ A.4+ A.5+ Total<br />
igation Tot. .8 Tot. S Tot. S Tot. S Tot. S Tot. S<br />
1958 725 521 16 77 18 11 10 1338 44<br />
1959, 558 2 186 17 22 14 775 33<br />
1960 646 2 618 17 37 15 7 7 2 .2 1317 43<br />
1961 1026 1 286 3 14 7 1 1 1 '1 1329 13<br />
1962 979 96 2 3 2 2 2 2 2 1082 8<br />
1963 724 342 3 20 8 10 10 1103 21 .<br />
Summe 4658 5 2049 58 173 64 31 30 5 5 6944 162<br />
8 = salmon with spawning marks [Summe = sum]<br />
v/<br />
In the age determination the salmon with spaipng marks have been<br />
incorporated inte the sea yeax classes according to the length of life they<br />
spent after their transformation into gmolt. Since the spawning maturity<br />
is dependent on the condition and thus can fluctuate annually and since<br />
the spawning fish are subjected for about one year to quite different<br />
2,3
•<br />
- 148-<br />
conditions of growth and wasting than the fish remaining behind, it becomes<br />
explicable that thé share of the salmon with epawning marks in each sea<br />
year class changes from year to year (Table 58). On an average the percen-<br />
tage of fish that have spawned increases with increasing years spent in<br />
the sea. The class of the fish with four winters (A.3+) is composed on an<br />
average of 37 per cent salmon with spawning marks. (The share fluctuated<br />
between 23 and 67 per cent from 1958 to 1963.) Of the older fish almost<br />
all salmon have already spawned.<br />
• This result leads us to the question about the number of the<br />
emigrating fish. If the sea year classes A.4+ and older consist already<br />
to about 100 per cent of fish that have spawned, then all salmon of the<br />
Lp. 317]<br />
Sea year class that have not yet spawned must emigrate in the spring of<br />
every year. With the aid of this statement and the Tables 33 and 37, the<br />
share of the emigrating fish can be estimated. For this end we start with<br />
the percentage age composition (Table 39, row 2). We know that the sea year .<br />
class .A.3+ consists to -37 per cent of salmon with spawning marks and we<br />
can assume that the remaining 63 per cent will emigrate-as A.4 and will<br />
epawn as A.4+. In the composition of the fish emigrating to spawn they<br />
• Table 39. Average percentage of fish of each sea year<br />
class that migrate annually to spawn.<br />
Sea year classes A.+ A.1+ A.2+ A3+ AA+ A3+<br />
Composition 1958-63, per cent 0,40 67,08 29,51 2,49 0,45 0,07<br />
Of these to spawn, number .00,98) 25,63 12,04 1,57 • 0,52 (0,115<br />
Per cent . 41 63<br />
account for 3 per cent (Table 37, last row)..With the aid of this relation<br />
it will beeasy to obtain the figure s . for the other age groups, e.g. 63<br />
Per cent of 2.49 = 1.57. Since 1.57 = 3 per cent (A.3+),.23 per cent is<br />
equal to 12.04 (A.2+) and 49 Per cent = 25.63 (A.1 -0, etc. According to
•<br />
- 149 -<br />
these results 38 per cent of the age group A.I+ emigrate (as A.2), 41 per<br />
cent of A.2+ and 63 per cent of A.3+ emigrate to spawn. These percentages<br />
have to . be viewed with reservations on account of the small number of<br />
salmon with spawning marks.<br />
5.3.2. Seasonal changes in the age composition<br />
Except for the fishing season 1960/61, WP have for every season<br />
in addition to the series of measurements in January also those for line<br />
catches in November and for net catches in April (Fig. 34). In January<br />
1963 no investigations could be made on account of the lack of fishing.<br />
Up to now we have evaluated the composition of the catch both according<br />
to the share in the brood --efapis--s4.)..ts and also according to the sea year<br />
yee.e-d& , , e, 4 s,iolt<br />
•<br />
classes (the y-e-a-r-1-..,--s-f—stte-1-t-). On a,ccount of the uniform growth con-<br />
ditions in the sea, the sea year classes are decisive for the fishing.<br />
'Hitherto statements could be made only for the investigations<br />
in january, because no scale samples had been taken from the fish of the<br />
other series of measurements. Although it is possible to estimate the<br />
share of the sea year classes with the aid of the frequency diagrams (Fig.<br />
34), there are no 'exact statements. In the age analysis after the method<br />
of Petersen it is necessary to select an arbitrary separation between the<br />
two maxima Of the frequency distribution that correspond to the sea year<br />
classes A.1+ and A.2+. When there exists no gap between the two classes<br />
on account of the different growth performance or on account of a very<br />
small share of the sea year class A.2+, this method of determination can<br />
cause an error of more than 5 . per cent, in some cases even one of more than<br />
10 per cent.<br />
For Obtaining the age composition of the samples of catches of
- 150-<br />
November and April of every fishing period a different method has been<br />
selected for the present case. At first glance the series of measurements<br />
for a season do not show any Considerable differences in the frequency<br />
distribution. The existing changes must be considered to have been caused<br />
principally by conditions of growth. Therefore the idea suggests itself<br />
to assume that the shares Of the two sea year classes in the transition<br />
zone of a series of measurements for all investigations of a season are<br />
almost equal. For testing this assumption the curve of the frequency dia-<br />
[P. 51 8 ]<br />
gram for November 1957 has been shifted until it coincided with the curve .<br />
for the distribution of.lengths of January 1958 (Fig. 35). Consequently<br />
it could be demonstrated that the series of measurements for November and<br />
January show about the same composition. The sea year class AJ.2+ of the<br />
series of measurements for April as a whole does not fit very well the<br />
series of measurements for April. This must be attributed to the smaller<br />
amount of growth of the older fish (see . 5.4.P.) and the selectivity of the<br />
nets. The gap between the two sea year classes thus becomes smaller.<br />
[p. 319]<br />
In Table 40 has been inserted the age distribution of the sea<br />
year class A.2+ in the transition zone, that has been obtained through the<br />
examination of scales. With the aid of these values can be ascertained<br />
now the age composition of the remaining series of measurements. If one<br />
shifts, for example, the series of measurements for November 1957 in such<br />
a way that coincidence is obtained With the distribution of lengths of<br />
January 1958, then there is seen a difference in lenghts of 4.0 cm between<br />
November and Jannaxy. Compared with the values in Table 40 this means that<br />
the salmon from Noveffiber 1957 belong exclusively to the age group A.1+ up<br />
to a length of 70.9 cm (2-cm-group 70). Of the 2-cm-group 72, 3 per cent<br />
- of the measured -fish belong into the age group.A.2+, of the 2- cm,group<br />
5. Per cent belong to to the. age group A.2+, of.that of 76, 14 percent,
•<br />
•<br />
Number of salmon<br />
J. en1967 872 Alli<br />
Angel<br />
Hook<br />
61111111ellibl■,<br />
Nov.1957 nil 1011 Alimmdie., Angel<br />
Jen.1956 1620MM Angel<br />
Lee---<br />
Apc1958 1390111W Metz<br />
hiAlLifit<br />
Nov1958 .22 Mpg Angel .<br />
Leaddikabb.....<br />
'<br />
Jon.1969 769MIR Mg.!<br />
Apt: 1959 575<br />
1111116111111111111116.--.-. —<br />
Metz •<br />
-..■1111111111 1 IMIlln..-.<br />
Now1959 740 Angel<br />
Jan.1960 1370111aWdhhhAigel<br />
Api:1960 564 Metz<br />
.111111111111111111Mbitur-<br />
Fig. 34. Composition by lengths of salmon caught in<br />
driftnets and by line.<br />
- 15 1 -<br />
and finally, of the 2-cm-group 90, 100 Per cent of the measured fish<br />
belong into the age group A.2+. The age composition for all series of<br />
measurements can be obtained in the same manner.<br />
It had already been pointed out that the gap between the -4wo<br />
maxima can be enaller in April. If the overlapping of the two groups<br />
increases, the transition zone in Table 40 would have to be enlarged.<br />
[p. 320]
... 103<br />
40<br />
so °<br />
60<br />
Lo<br />
Jan Kt 1.192 , Anititi -<br />
Nov 961 1186 Angel<br />
Jan. 962 1224 Angel<br />
Ape<br />
' .<br />
962 714 Netz<br />
Net<br />
•<br />
Nov. 962 .997 Ange In<br />
Apt: 1963 1103 Her<br />
Nov. 1963 . Netz<br />
60<br />
80<br />
Fig. 34, continued.<br />
100cm Tafflimm .<br />
Total length<br />
7 152 -<br />
Such regrouping of the percentage values is, however, difficult and<br />
necessarily faulty. It is therefore suitable . to project the series of<br />
meaSurements for April in such a way that•not the maxima of the age group<br />
A.1+ coincide, but the two.minima between the age groups.<br />
Let us now compare the age composition of the catches of Novem+<br />
ber and January of every fishing Season (Table 'ii). In all cases there is •<br />
'excellent agreeMent for the share of the sea year class A.1+. The difference.<br />
between the two values is in each case only 0.2 to 0.5. Such a* difference •
4.<br />
number<br />
50<br />
e"<br />
•<br />
);<br />
e<br />
e ,<br />
lot<br />
nb<br />
• •" Novondet 1.957<br />
1951<br />
Apnl 9151<br />
7 153 -<br />
..110 one Tocolkinq Jort19‘<br />
Totalkinge, Nov19bi<br />
Tota!k,nge,April 151<br />
• _<br />
Total leegth<br />
Fig. 35. Composition by lengths of German salmon catches 1957/58.<br />
(Frequency diagrams of November and April superposed on the<br />
distribution by lengths of January).<br />
can have its cause in methodology so that we may assume the same age com-<br />
position for November and January during every fishing period.<br />
Matters are different for the series of measurements for April.<br />
In comparison with January, the.catches investigated show higher figures<br />
in two cases and in two cases the figures are lower, and in'one case the<br />
values for the age group A.1+ are about equal. Especially outstanding are<br />
the percentages of April 1960 . and of 1963. How can this be explained?<br />
- It has already been said that the maturing salmon start their<br />
spawning migratioris already in spring. This behaviour has the effect to<br />
raise the percentages for A.1+. The percentage of the age group A.1+ is<br />
going to change in relation to January depending whether the salmon do not<br />
yet begin their migration already in April snd move northwards in only small<br />
numbers, or whether they move already in large numbemintothe rivers at<br />
this time.<br />
• On the other hand, the catches in April that have been inves-<br />
tigated were all taken in nets. According to the curves for selection in<br />
Fig. 10 a numbei, of smaller salmon of the age class A.1+ are not being
70<br />
2<br />
4<br />
6<br />
4<br />
1<br />
7 154 -<br />
caught together with the others, whereas in regard to the age class A.2+ .<br />
the selection is, almost complete. This has the result that the percentage<br />
of the fish of two winters in April is.lower than in November andJanuaxy<br />
when the fishing ià done with hoekS.• •<br />
Now, it has been shown that the age composition of the -catches<br />
in November and Januaxy of every. fishing season is the saine, whereas in<br />
the Spring.it will be'influenced through the emigration of the large sal-<br />
mon on one hand and by selection on the other. Both causes act in opposite.<br />
[p. 321]<br />
direction. One can therefore assume that in April 1960 the emigration of<br />
the older fish was predominant,.whereas in April 1963 the effects of selec-<br />
tion were decisive. .<br />
Table 40. Composition by age in the" transitional sene of<br />
. lengths between the sea year classes A.1+ and A.2+.<br />
Lt Number . of salmon of the sea year class A.2+ . in<br />
. per cent of the total number of one length . class<br />
cm Jan. 1958 Jan. 1959 Ja.1960 Jà.1961 Ja.62 Apr. 63<br />
8 ' . 5, 3 , 12 3 1 4<br />
80 . 14 8 50 5 3 • 4<br />
2 16 ' 13 • 60 14 3 21<br />
4 33 27 • 81 35 6 39<br />
• 6 53 30 91 73 10 45<br />
8 . 74 69 100 87 35 82<br />
90 89 87 96 60 100 • .-<br />
2 98 95 100 100<br />
100 100 . 95<br />
95<br />
[p. 322]<br />
5.3.3. The age structure of the exploited stock in the main basin of the<br />
the Baltic Sea<br />
• Hitherto have been given the results of analyses of the ages<br />
of entire catches. However, it has not been discussed whether these<br />
catches can be considered representative of the total landings and whether
they take account of the annual changes in the stock.<br />
- 155<br />
•L<br />
It is very diffult to find,,the age composition of the total yields<br />
with the aid of the above results. Kàndler has indeed introduced a statis-<br />
tics with six groups of weight (1-2 kg, 2-3 kg, 3-5 kg, 5-7 kg, 7-8 . kg and<br />
pver 8'kg) for the landings at the Kiel Seafish Market, in which all sal-<br />
mon are regiStered numerically (R. Kândler and M. Lâhmann 1957). Kândler<br />
(19 6 1, 1963, 1964) has used the distribution of the groups for obtaining<br />
the age composition. However, a division of the fish landed into the tWo<br />
most important sea yearcaasses A.1+ and A.2+ with the aid of these statements.<br />
is, however, necessarily subject to errors. This is owing to the annual diem.<br />
ferences in growth and to changing sharesof the sea trout. In Table 19 it<br />
had been shown that the percentage of sea trout in the catches varies<br />
greatly and has amounted to an average of 3 to 15 per cent during indiv4.<br />
idual fishing seasons. It is difficult to eliminate these fish because they<br />
are not listed separately in the figures for the yields and their share<br />
in the individual groups is not fixed.<br />
'A division of the.salmon landed with the aid of the statistikos<br />
9f the catches can be carried out in such . a manner that the fish under 5 kg<br />
weight are assignèd to seai.year class A.1+ and the heavier fishto 1.1ti<br />
The actual boundary isectordin:g to wsight . between the twO grouPs‘is, however t<br />
not constant. It shifts during the course of every fishing season as well<br />
'as from season to season.<br />
It is possible to estimate the errors that OCCUT when the age<br />
• composition is determined with the aid of the statistids of the landings.<br />
This c an be done in the following manner: the complete catches that have<br />
been investigated are being divided according to the weight of the fish.<br />
TheSe series or measurements contain also seà trout (Table 42, colleen 3).
Table 41. The composition by age of the German salmon<br />
catches in different months and years in per cent.<br />
- 156 -<br />
Season Month Number of Sea year class<br />
salmon A:+ A.1+ A.2+ ( 11 .3+)+ (A.2+)+<br />
1956/57 Januar 872 77,2 22,8<br />
• 1957/58<br />
November<br />
Januar<br />
April<br />
1090<br />
1620<br />
1398<br />
0,3<br />
54,0<br />
54,2<br />
57,5<br />
39,0 6,5<br />
46,0 ,<br />
45,5<br />
42,2<br />
1958/59<br />
November<br />
Januar<br />
April<br />
823<br />
789<br />
577<br />
1,2<br />
72,5<br />
72,0<br />
71,4<br />
24,0 2,8<br />
26,9<br />
26,8<br />
28,6<br />
November 749 48,7 51,2<br />
1959/60 Januar. 1318 0,5 49,1 46,9 3,5 ' 50,4<br />
April 527 57,0 42,8<br />
• 1960/61 Januar . 1324 0,1 77,2 21,5 1,2 22,7<br />
November 1161 . 90,0 10,0<br />
1961/62 Januar 1225 90,5 8,9 0,6 9,5<br />
April 699 88,2 11,2<br />
1962/63 November 997 74,6 25,4 '<br />
April 1112 0,6 65,7 31,1 2,6 33,7<br />
IIMMOReemol.■••••••111•■•••■••••■■■••■■•••••■•••••••■■■<br />
If one now ascertains the percentage of all salmonids that weigh less than<br />
5 kg,(Table 42,'column 6), one obtains values that have been got according<br />
to the method of Kândler (19 6 1, 19 6 3, 1964). When one compares these results"<br />
with those arrived at through the examination of scales, one finds ,:conbid-<br />
erable deviations that exceed the allowable limite of error (Table 42, column<br />
8). It is not possible to apply exact corrections to the data as long as the<br />
share of the sea trout in the statistical figures is not known. In regard<br />
to the errorErnaused by changes in growth only a very coarse and uncertain<br />
improvement can be made even with the aid of series of measurements. This<br />
method is thus not suitable for an exact analysis. It is, Inwever, of value .<br />
when one wants to obtain a preliminary general view of the stock conditions<br />
quickly - without tedious collecting of sample's and time-consuming examin-•<br />
ation of scales. In this paper no comparison has been made between the<br />
samples of catches investigated and the total landings. It will therefore<br />
•be clarified . in. a different manner in how far the fluctuations in catches
•<br />
-157-<br />
and in the stock are being reflected in the series of measurements pres-<br />
ented. In order to make obvious the regular changes, the general results'<br />
of the investigations will be summarized here (cf. Table 41). During a<br />
fishing season the stock is represented substantially by two year's Sets<br />
of gmolt x and x - 1, that appear as pea year classes A.1+ and A.2+. Both<br />
are represented in the catches of November and January as well as in those<br />
of April 14 . In the succeeding fishing season a new year's set of gmolt<br />
has entered the exploited phase, which forms the new pea year class A.1+.<br />
[P. 323]<br />
It has come neifly into the exploited stock during the time between summer<br />
and fall. On the other hand, the year's set of gmolt x aPPears now.as the<br />
sea year class A.2+ , . whereas only few fish of the year's set x - 1 are<br />
being caught. They have already started their emigration to the spawning<br />
grounds in the spring of the previous season. This annual change. in the<br />
stock has already been touched during the dicussion of the yields (2.3.4.).<br />
Since the renewal of the stock mentioned may not be « quite com-<br />
pleted by the beginning of etery fishing season in August/September and<br />
since new changes take place through emigration in spring, one can consider<br />
the composition of the stock to be unchanged only during the period from '<br />
about November to karch. It is therefore appropriate to use this period<br />
as the basis for comparing the age distribution from season to season.<br />
.These reflections are confirmed by Table 41. Since . the share of the sea<br />
year class A.1+ in the samples of catches of November and January of each<br />
season is the same,.We may assume that these series of measurements detect<br />
.the rather unchanged conditions from November to March.<br />
The questions of the aboVe sections concern the relation between<br />
14 The two classes would have to be designated correctly as A.2 and A.3<br />
in the April'catches, because the years are completed at this time.
Table 42. Share of the sea year class A.1 in the catches, obtained at the one hand with the<br />
aid of the landing figures (weight groups) and on the other hand<br />
obtained through examination of scales.<br />
Date of Number of Of these sea trout Sàlmon with Salmon a. sea trout P.c. sal- Difference<br />
salmonids<br />
examination examined Total ..c5 kg<br />
spawn. mark
Table 43. Mean lengths of age groups and sea year classes in cm total length, Baltic Sea.<br />
ige . January 1958 January 1959 January 1960 January 1961 January 1962 April 1963<br />
group Num. ay. lgth. Num .. av. lg. Num. av. lg. Num. av. lg. Num. ay. lg. Num. av. lg.<br />
•<br />
1.+ 2 51,0 • 1 56,0<br />
2.+ • 4 46,5 46,5<br />
3.+<br />
5.+<br />
1.1 + • 30 70,2<br />
• 2.1 + 249 720<br />
3.1 + 381 73,1 72,6<br />
4.1 + 60 74,4<br />
•5.1 + 5 70,5<br />
. 1.2 + - 34 92,2<br />
• 2.2 + 273 95,6<br />
. 3.2+ 191 97,6 96,2<br />
4.2 + 21 99,2<br />
5.2 + 2 95,3<br />
1.3 + 8 98,0<br />
2.3 + 43 102,9 102,9<br />
3.3 + 25 104,5<br />
4.3 + • 1 94<br />
1:4+<br />
• 2.4 + 7 108,5<br />
3.4 + 4 106,5 107,8<br />
4.4+ •<br />
4 46,8 49,2<br />
2 ,47,5<br />
1 58<br />
23 74,9<br />
174 74,4<br />
257 75,9 75,8<br />
• 94 77,5<br />
10 83,1<br />
21 91,6<br />
59 92,4 •'<br />
93 94,3 93,5<br />
11 96,0<br />
2 91,5<br />
4 102,3<br />
11 102,3 102,4<br />
7 102,5<br />
*<br />
3 51,2 52,5<br />
•<br />
• 2 52,4<br />
1 53<br />
44 73,5<br />
193 '73,5<br />
331 73,2 73,5.<br />
71 74,4<br />
7 78,4<br />
63 95,2<br />
212 96,7<br />
256 97,2 97,0<br />
84 98,3<br />
3 100,3<br />
5 106,8<br />
16 107,4 107,7<br />
15 108,1<br />
1 110<br />
1 109<br />
4 111,7<br />
2 108,8 110,5<br />
1 42 42<br />
35 77,6<br />
187 79,7<br />
677 80,7 80,5<br />
74 82,3<br />
12 85,1<br />
42 94,6<br />
91 94,2<br />
149 95,1 94,9<br />
15 97,3<br />
7 109,0 105,1<br />
6 100,3<br />
• 3 98,5 99,9<br />
1 102<br />
•<br />
48 72,7<br />
252 73,9<br />
509 76,3 75,5<br />
144 76,3<br />
26 76,6<br />
21 90,9<br />
33 95,8<br />
42 97,0 95,3<br />
1 105<br />
2 103,5 103,5<br />
2 114,5<br />
114,5<br />
1 54 59,2<br />
3 58,5<br />
1 62<br />
2 62,0<br />
37 75,7<br />
283 73,7<br />
264 74,3 74,3<br />
56 76,4<br />
3 73,8<br />
26 92,4<br />
115 94,4<br />
116 96,1 95,1<br />
13 96,5<br />
1 100<br />
6 101,0<br />
2 102,5 101,4<br />
11 102,6<br />
1 88<br />
1 105<br />
3 103,8<br />
.6 103,8 103,9<br />
1.5+ ' 1 115 •<br />
1 117<br />
2.5± •<br />
1 117 115,6 1 128 128 1 126 121,0<br />
•
•<br />
- 160 -<br />
the composition of the samples of catches, of the landings and of the [P.325]<br />
stock. Changes in the composition of the landings are shown clearly in<br />
Table 17. This table shows that the average weight-'of the salmon rises •<br />
in the mean of the years 1954 to 1964 from September until about Febm-<br />
ruary and that it thein•dropsé. The increase must - be considered to . be a<br />
result of the growth, the decrease must be considered td be an effect of<br />
the emigration of the large salmon. Changes in the composition of the<br />
landings are thus caused only through the spawning migration. These findings<br />
agree with the results of the investigations of samples as well as with<br />
the conditions in the stock that have been described above.. Since in each<br />
series of measurements on an average more than 1000 salmon-Of comPléte<br />
datches have been examined, we may consider them to be largely represen+<br />
tative for the landings. It is a different questionwhether this agreement<br />
exists to the same degree in regard to the exploitable stock. Although<br />
changes in the stock find expression also in the samples of eatches, it<br />
cannot be proved that the percentage age . composition of the series of<br />
measurements agrees with that of the exploited stock. Nevertheless, it be-<br />
comes clear that the reèults of the analyses of the series of measurements<br />
for January shown in 5.3.1. (Table 33) provide considerable information<br />
about, the dynamics of the stock of salmon in the Baltic Sea and that they<br />
do reflect the changes in the exploited stock of the southern Baltic Sea<br />
(cf. 7.4). •<br />
It hae already been pointed out'that it was not possible to<br />
take scale samples in January 1963 on account of the ice conditions in the<br />
Baltic Sea. This could be done only in April 1963. This sample éag, however,<br />
not considered to be representative, as has just been shown. In its stead<br />
'the series of measurements of November 1962 had to be used. The age composition
•<br />
- 161 -<br />
of these catches has been ascertained with the aid of Table 40 and of the<br />
results of the age analyses of April 1963. With the use of the values from<br />
Table 40 it waS possible to include the age composition of the series of<br />
measureMents of January 1957 in the results (Table 33).<br />
5.4. The growth relations<br />
Investigations of the size of the ascending salmon of the Baltic<br />
Sea have been made by T. H. arid (1938 , 1948), G. Alm (1934), J. Jokiel<br />
(1958) and M. N. Lishev and E. J; Rimsh:(1961). The extraordinarily large<br />
material of Jgrvi (more than 60,000 salmon) has recently again been treated<br />
statistically by A. Lindroth (1961a).<br />
The first investigations of the growth of the salmon in the<br />
southern Baltic Sea were made by A. Willer and W. Quednau (1931), P. Brandt-<br />
ner (1938) and B. Dixon (1934). The small material on which these inves-<br />
tigations Were based was sufficient to give a first, valuable View of the<br />
growth performance of the salmon. The data are, however, not sufficient<br />
for a comparative treatment. Only F. Chrzan (1959b), R. andler and M.<br />
Lehmann (1957) and F. Thurow (1960) investigated a larger material that<br />
was suitable for cdmparisons.<br />
5.4.1. Results of the investigations<br />
The, results of the preseht investigation . have been summaxized<br />
. in Table 43. The results apply only tO the life in the sea.<br />
It has already been pointed out that the two maxima that appear<br />
in the series of measurements (Fig. 34). represent the two important sea<br />
year classes A.1+ and A.2+. The age determinations confirm this. It is seen<br />
that the salmon of two winters have in January of the years of investigation
mean total lengths of 72.6 . to 80.5 cm, whereas those of three winters had<br />
lenghts of 93.5 to 97.0 cm. These measurements agree excellently with the<br />
maxima in the series of length measurements.<br />
100<br />
0,7<br />
cm<br />
rotoffin g e = total length<br />
...,-,:elie,<br />
Alemproe_ -:_<br />
, ,/ xi,<br />
.ir<br />
„...,<br />
, ,/<br />
,<br />
, ,<br />
, ,,<br />
, , ,<br />
, , ,<br />
, „ , ,<br />
, , , , , ,,<br />
, , , , , ,<br />
,<br />
, ,<br />
, , , .<br />
. . ti)t<br />
.<br />
m) m) (I) (.e ' r (.1<br />
x t flS V VIS<br />
XI<br />
A. I.<br />
nu mu nu nu 1961 nu<br />
Year of examination<br />
A 2.<br />
1963<br />
Untersuchungsjahr<br />
• it.. - ttai<br />
Fie. 36. Longitudinal growth of different yca7 t s ccts of<br />
smoi-t-of Baltic Sea salmon.<br />
Months<br />
t I t I<br />
4-4<br />
vet ex ere e PtIonatt<br />
3 4 liettrjohreskla sun<br />
- - •<br />
Sea year classes.<br />
Fig. 37. The average changes in the length-weight<br />
coefficients K for the ye.epele-se-t of smolt of 195 6 to 60 .-<br />
Let » us now follow the loagitudtnali g„. 22t12 of the yeares, st<br />
- 162<br />
-<br />
•<br />
CÂMSeS<br />
[p. 326]
- 163<br />
-<br />
of enolt in Fig. 36. From an assumed length of the smolt of 15 cm the<br />
growth curves rise steeply during the first year. In the following.years<br />
the curves flatten out. The greatest length ohserved was 128 cm. Corres-<br />
ponding to this course of the curves the rate of• growth is greateét in<br />
the first year and after that.diminiéhes steadily. The increase in length<br />
during the first year is on an average over 30 cm, during the second year<br />
about 28 cm, in the third year about 20 cm, in the fourth year about 8.3<br />
cm and in the fifth year about 5 cm.<br />
( SV1N et,v- 46,g) [p. 527]<br />
It may be assumed .that of the sea year class A.+ only the<br />
largest fish had been caught, so that the mean length is actually lower •<br />
than the values in Table 43 show. The difference is, however, probably<br />
not very great. G. Nordquist (1908)'carried out in April/May 1905 to 1907<br />
length measurements on salmon in the Màlm8hus Lân that had been.caught with<br />
narrow sand-eel . nets. bf the 168 fish 151 were under 60 cm long and ob•r<br />
viously belonged . to.the sea year class A.1 (of one winter). These fish had<br />
. a mean length of 47.0 cm. He furthermore cites .a series of measurements<br />
by C. V. OtterstAil that was done in April/Mày 1906 on Bornholm :The 159<br />
fish of the age group A.1 had a Mean length of 47.6 cm. From this can be.<br />
deduced that the,èrror of the stated lengths of the one-wintèr salmon in<br />
36 and Table 43 is not very large.<br />
The growth in weight takès a course quite different from that .<br />
in length. The smallest increas&df about 1 kg is found during the first<br />
year. After a greater increase during the second year (more than Lkg gain)<br />
the highest growth rate is achieved during the third year with more. than<br />
4 kg..During the following years the increase is again smaller.(in the<br />
fourth year over 2 kg, in the fifth year less than 1 kg)(Fig. 38)..<br />
F. Chrzan (1959b) arrived at similar resultein regard . te. the<br />
Fig.
Schlaçhtgewicht<br />
kg •<br />
1957<br />
Fig. 38.<br />
gutted weight<br />
e<br />
.<br />
/<br />
--- 1<br />
• i_<br />
1958 1959 1960. 1961 1962 Jahre irea-rm:<br />
Weight increase in the Baltic Sea salmon.<br />
- 164<br />
-<br />
increase .in weight. He found that the salmon showèd the greatest increase<br />
thiring the third year in the sea. The investigations of the length, how-<br />
• evsr, showed the gredbast increase during the second . year in the sea - in<br />
contrast to the results given above. The same result was obtained by Kând-'<br />
ler and Lfihmann (1957): Chrzan obtained the mean lengths with the aid of<br />
a simple recalculation (cf. 5:2.2.). Furthermore hiasamples of catche,<br />
as well as those Of Kândler and ahmann, were not taken at a certain date,<br />
but durinithe entire season. It is therefore not possible to make a Closer<br />
. comparison between the iesults of these authors and of those of the present<br />
investigations.<br />
•<br />
The Figs. 36 . and 38 show, the characteristic annual course of<br />
growth very plainly, the rapid increase during the summer and the check<br />
[p.528 ]<br />
in the winter. These differepées are the more distinct .theyounger'the<br />
fish. In the older salmon a slowing down of growth during the winter is •<br />
hardly perceptible.<br />
A comparison of the growth in length and weight . shows that the
--165 -<br />
increase'in weight is more retarded dUring the winter than the increase<br />
in length. The •two different processes, the predominance of the increase<br />
in weight in summer (rise in condition) and the predominance of the in-<br />
crease in length (loss of condition) in winter regulate the changes in<br />
the length/weight coefficient K (Fig. 37).<br />
•Yeefe - ei"-s 5<br />
. If one follows the performances of each individual yeer-Le-ect,<br />
one finds - very different. forms of the course of- growth (Table 44). The<br />
'yeef-a.sse • -<br />
yeaele,--s494e 195 6 and 1961 attained as•sea year class A.1+ in November the<br />
Very small average length of 68.7 and 68.3 cm, respectively. In contrast,<br />
all other ye-aels. were already over 70 cm long in November as A.1.<br />
Thus the yee,r'o act of.smolt of 1957 had a length of 74.1 - cm as A.1+ in<br />
•November and so was 5.4 cm longer than the year's set of 1956 in the<br />
s.<br />
previous year. The yeeple-set of 19 5 6 managed to reduce this difference<br />
to 1 cm, bees:Use it had Made an average gain of almost 9 cm in length.<br />
yek.m-e..144:<br />
On the other hand the year's cot of 1961 grew during the winter by only<br />
6 cm and that of 1960 even bY only 4 cm. Especially outstanding is the<br />
performance of the et1=tj4t of smolt of 1959 that has been peinted Out<br />
. by Kandler (1961). This ye,aele-ae4 was 80.5 cm long as A.1+ in January .<br />
1961 and had thussgrown at least 5 cm more than any other e444-%-e4<br />
Surprisingly, this advantage finds no longer an expression ,in the4ssea<br />
Year - claas A.2+ (1961/62).<br />
• The growth in the sea is dependent predominantly.on the duration<br />
of the -sojourn in the sea. As is 'shown in Table 43, the influence of the<br />
brood year's oc t is still plain; because the mean lengths increase in<br />
general witnin . a sea year class with increasing duration of the stay in<br />
' the rivers. On an average, during the years 1958 to 1963 the difference<br />
- between the'age groups 2.1+ and 3.1+ is about 1 cm. This phenomenon has
- 166 -<br />
already been pointed out several times (T.H. Jgrvi 1938,.B. Dixon 1954 ,<br />
F. Chrzan 1959b, F. Thurow 1960).<br />
5.4.2. Discussion of the findings<br />
A. Lindroth (1961a) has ascertained in his extensive analysis<br />
of the iaaterial of Jârvi that the size of a fish at a certain age is det-<br />
ermined by font. factors,.namely, the genetically fixed growth potential,<br />
the intake of food, the chemical and physical environment (especially tem-<br />
perature) and'the initial size that it had at.a certain time. The last<br />
point is obviously valid only when a limited period of life is under con-<br />
sideration. As in the present case, the life of salmon in the sea. Apart<br />
from the innate growth potential the three points are not primary factors.<br />
In . their changes they are rather subject to other factors. Thus, for ex-<br />
ample, the intake of food depends on the numbers of prey available, on the<br />
time of their appearance and on the number of competitOrs for the food.<br />
5.4. 2. 1. The rate of growth<br />
Before we consider some phenomena that are indicated'by the<br />
matérial presented, the general features of the growth process must be<br />
reviewed. The course of both the increase in length and in weight shows<br />
that the rate of growth dScreases considerably during the fourth year in<br />
. the sea. It is a general feature Of fish that they grow during their,entire<br />
life. Only in rare cases, when they, are forced to cease feeding, is it<br />
possible for the weight to decrease. .<br />
11). 329]<br />
In the treatment of the salmon with spawning marks it has been<br />
éstablished that the sea year class A.3+ (that of the fourth year in the „<br />
Baltic Sea) cc:insists already . Of 37 per cent of salmon with spawning marks.. .<br />
•<br />
• 0
•<br />
rl<br />
-P<br />
b..0<br />
-e<br />
nzi<br />
-ri<br />
r-1<br />
gl<br />
a)<br />
of smo lt, to tal<br />
Table 44. Growth of .<br />
\ID<br />
o<br />
Cr■<br />
.I.fl<br />
a Ln 0 Ln<br />
»,-11 ■In' '2 4-'.: -›'.<br />
A marks and 110.8 for those fish<br />
that had not yet spawned. In<br />
January 1961 these lengths were even 93.8 and 109.3 >cm, respectively. In
- 168-<br />
spite of the changes that the curve of growth undergoes when the fish<br />
are being eliminated that have aiready spawned, the reduction in the rate<br />
of growth in the older fish can be demonstrated ..<br />
In a paper On the fluctuations Of quality in the Baltic Sea<br />
salmon (F. Thurow 19 62) it could be shown that at a certain body length<br />
[p. 330 ]<br />
the salmon have finished a decisive phase in their development that serves<br />
as preparation for the spawning migration. Since most of the maturing fish<br />
have emigrated before the third year in the Baltic Sea, it suggests itself to<br />
consider here the salmon of the class A.3+ to be such fish that had in<br />
the previous year just failed physiologically to obtain the readiness for<br />
. the spawning migration, beCause they had not reached the condition neces-<br />
sary for the Spawning migration.<br />
5.4.2.2. The growth of the year's set of smolt of 1959<br />
n the preceeding it has been demonstrated that the-<br />
of gmo•t of 1959 as sea year class A.1+ had attained an outstanding mean<br />
lengthof 80.5 cm. A length that had not been attained by any other year is<br />
etss<br />
---sigt for a long time (Tablas43 and 44). The salmon of two winters that had<br />
been examinalby Kgridler and Whmann (1957) had in 1952 to 1955 lengths of<br />
69 to 73 cm. F. Chrzan (1959b) found, it is true, a corresponding mean<br />
length of 80.6 cm. However, he could examine only 16 salmon of this sea<br />
year class A.1+. Furthermore it has' not beenstated whether. the material •<br />
examined originated in winter or spring. In any case the growth of the<br />
e.,Le5<br />
year's ..sre4t of smolt of 1959 deserves a closer examination.<br />
T. H. ervi had pointed out in 1948 that the mean size . of all<br />
salmon had diminished considerably since 1942 to 1944. According to Lind7<br />
. roth (1961a) this reduction became obvious for the first time in the year%
- 169 -<br />
CLA‘s<br />
set of smolt of 1939. He could show that the limited annual fluctuations<br />
of the mean lengths were highly significant, but that they had little to<br />
do with the changes since 1939. Lindroth is of the opinion that changes<br />
in growth are caused by factors that are effective during the first.year<br />
in the sea. Food together with population density, as well as temperature<br />
conditions are cited as possible causes. A previous reduction in the length<br />
of the smolt is not being excluded.<br />
aess<br />
Let us now follow the growth of the vearts. -b-et of 1959. A mean<br />
see5<br />
length of 80.5 cm means::anincrease over the mean of the year's Set.s of 1956<br />
to 1961 of 6.7 cm (9.1 per cent). In contrast to this the weight increases<br />
by 38.6 per cent tc4.17 kg. This shows that this.growth performance is not<br />
only of scientific interest but also of commercial interest. By taking as '<br />
basis the age composition of the catches 1960/61 it is seen that the yield<br />
CIA.ss<br />
in weight bythe mean weight of the sea year class A.1+ (yeails-Bet of smolt<br />
of 1959) ivas 22.3 per cent higher than it would have been for a "normal"<br />
mean weight of 3;01 kg.<br />
.What did cause this good growth? The sea year classes A.2+ and<br />
A.3 + that appeared together with the yearis of smolt of 1959 in Janu-<br />
ary 1961 did not show an especially good growth. It must therefore be as-<br />
• not<br />
Slimed that the phenomenon did/affect uniformly all age groups that appeared<br />
at the same time, but that it was caused by an effect that influenced only<br />
C6.-css cbt.ss<br />
a single yeaeb,sSt. When one follows the yeart backwards, it Can be<br />
de.s$<br />
shown that the year"s,>e,„t of snolt of 1959 probably had grown well also<br />
during the first yearin the Sea.(Fig. 38).<br />
We face now the question, in which stage of life the special<br />
' increase in growth had been realized for the first time. Let us consider<br />
• in this connection the following three possibilities:
- 170-<br />
(a) the good grciwth . of the year'aet of smolt of 1959 took place for the<br />
cf.4e,s<br />
first time in the sea. All age classes of this year'e set must then<br />
dees<br />
have grown very well . No' age group of other yearPss, ee ts should show<br />
a similar result.<br />
(b) The good growth was induced already in the rivers. Only one brood yearm-fd<br />
has grown up under optimum conditions and has later as one of the<br />
age groups 1.B to 5.B exerted a decisive influence on the mean length<br />
ae,“<br />
and the mean weight of the year",>s 'eet of smolt of 1959: The other age<br />
groups do not show such outstanding results of growth.<br />
d. [p. 331]<br />
(c) The good growth was induced in the rivers. Several brood years ee4s<br />
did live under favoilrable conditions and constitute the cause of the<br />
CIAS<br />
good growth of the year"R--eet of smolt of 1959. Therefore, several of<br />
its age groups show special gains. Since the age groups in question<br />
did not only contribute to the formation of the year's, 'eat of smo.1À<br />
of 1959 , but formed also age groups of other year's eets, these.also<br />
should shoW good results.<br />
• eisv-6ie't4S<br />
Let us now follow the brood yeerem-ee4s during the corresponding<br />
cLees<br />
years. The age groupS of the year'sr-eet of smolt of 1959 are made up of<br />
c-1,,Ç es<br />
parts of the five lœood year't-rete 1954 to 1958.<br />
-ctas4cs<br />
As is shown by Table 45, four of these brood year'b bets take<br />
-ciass<br />
part in the formation of the . yearl-e-eet of smolt of 1958. If growth-prom-<br />
oting influences were active in the rivers during the period cited, then<br />
they Should be apparent almost as strongly in the yearie-tôf-âmet'.of<br />
1958 as in that of 1959. Let us inspect Table 43 in this connection and .<br />
-d&ases<br />
compare the mean lengths of the age groups of the year 's-re-S. of smolt of<br />
1958 (January 1960, age group 1.1+ to 5.1+) and of 1959 (January 19 6 1,<br />
elos<br />
age groups 1.1+ to 5.1+). It is seen that the fish of the yeare-e-eet of<br />
•gmolt qf .1958 are very much smaller and show in comparison with the age
Year's sets<br />
of smolt<br />
CILS<br />
present<br />
7 171 -<br />
groups of the yearem-sst of smolt of 1959 the very great differences in<br />
length of 4.1 to 7.9 cm.<br />
•<br />
Table 45. Brood year's sets that appeared together in the<br />
rivers during the years 1954 to 1959. •<br />
1955 1954 1953 1952 1951 1950.,<br />
1956 1955 1954 1953 1952 1951<br />
1957 • 1956 1955 • 1954 1953 1952<br />
• 1958 1957 1956 1955 1954 1953<br />
•<br />
1 ,)59 1958 1957 1956 1955 1954<br />
1960 • 1959 1958 1957 1956 1955<br />
For the sake of completeness let us also inspect the yeart'u<br />
-of smolt of 1960. In case the decisive factors were active only in the<br />
year 195 8 , then the brood year4ASs4ise.. of 1954 tà 1958 have been 4fluenced<br />
ekts<br />
. by them. That means, however, that apart from the year'b bet of 1959, the<br />
.year‘s--met of smolt of 1960 also would have profited by it, because four<br />
of the affected brood year's-sets took part in its formation. Let us there-<br />
fore examine also the mean lengths of this yearLs-set of smolt in January;<br />
clAss<br />
they are 4.4 to 8.5 cm lower than those of the year"r-sset of smolt of 1959.<br />
. Let us .now attempt to obtain a last pointer for the answer to<br />
this question. From Table 33 can be seen that the yearl-s-sst of smolt of<br />
1959 . as A.1+ contained 63.5 per cent of three-year-old smolt, wheras the<br />
proportion of these in the year -"s-set of, 1960 was 52 per cent. When one<br />
now obtains through simple recalculation the lengths of-smolt for these<br />
brood \eallâai that are represented most strongly, one obtains 14.4 cm<br />
for the former and 15.3 cm for the latter, that is a smaller length for<br />
- cl.ss<br />
the main component of the year's-*et of smolt of 1959.<br />
According to these statements it must be considered to be most
- 172 -<br />
improbable that the promotion of growth took place already in the rivers.<br />
, The decisive impulse was received rather certainly during the first year<br />
yeme-c..4,43<br />
in the sea (1959). However, at this time the .scri-s—set of smolt of 1958<br />
was also represented in the Baltic Sea (as A.14.), which did not show any<br />
very great growth. One must therefore assume that special circumstances<br />
did influence the year's-set of smolt of 1959.<br />
Let us examine once again from this point of view the four<br />
factors that influence the growth, mentioned earlier. A change in the<br />
growth potential can here be excluded. The influence of the initial size<br />
must also be denied according to the above statements. It is furthermore<br />
true that the post-smolt could not have lived under different conditions<br />
of tekperature or thet they were influenced by them differently than the<br />
larger fish. Thus there remains as decisive influence the complex factor<br />
of 'food.<br />
' A. Lindroth (1961b) has shown that the young salmon feed in the<br />
sea at first on flying insects and pursue fish only later. According to<br />
our investigations (2.2.3.2.) salmon of a length of hardly 30 cm take<br />
already the baited hooks. The size of the maeh opening certainly plays<br />
a role in the trabsition to fish food. At this time the young fish are<br />
living already under the same conditions as the Older salmon. For this<br />
dass<br />
reason we assume that the extraordinarily good growth of the yeart-s—ee.t..<br />
of smolt Of 1959 had as its cause' the excellent supply of food fbr the<br />
post-smOlt during the first period of their stay in the sea. Thus the<br />
same factor (food supply) is responsible for the unusual growth of the<br />
yearLe—sett of Smolt of 1959 as that cited by Lindroth as the cause of the<br />
c,14es<br />
very poor growth of the year's-set of 1939.<br />
HoWever, before this question can finally be settled it is<br />
[P. 332]
- 173 -<br />
necessary to follow the growth beyond the sea year class A.1+. Here, how-<br />
,I)ew-c,144s<br />
ever, it is found that the year's-ret of smolt of 1959 as sea year class<br />
À.2+ does no longer show a sPecial size. This phenomenon cari be explained<br />
only by the fact that very many, and especially the laxgeet fish have al-<br />
ready emigrated after a stay in the sea of only two years, in order to<br />
spawn in the fall/winter of 1961. The increase in the Swedish river catches<br />
from 110 t in 1960 to 209 t in 1961 provides a hint for this assumption.<br />
5.4.2:3. The influence of the size of smolt on the growth in the sea<br />
It has' already been mentioned:that the smolt are the larger, the<br />
longer the duiation of the sojourn in fresh water and that these differences<br />
Can.still be observed in the adult fish in the sea. Lindroth (1961a) alao<br />
has investigated this question. He arrived at the result that an influence<br />
of the smolt age on the size of the adult salmon could not be proved as<br />
significant in 13 outof 14 cases. Seen from a certain point Of view, it<br />
.seems to be of value, to examine this question.once more on hand of the<br />
• German material of observations.<br />
With the aid of Table 43 we can ascértain the mean annual in-<br />
crease in the age groups 2.2 and 3.2 (the difference between 2.2+ and 2.1+,<br />
and between -3.2+ and 3.1+) and we obtain values of 20.00 and 20,01 cm.<br />
A rate of growth .that agrees that closely for thé two most important age<br />
groups 2.B and 3.B indicates that differences in the mean lengths that<br />
exist already, remain in existence also in the sea.<br />
An important hint, regarding the question,.whether the size of<br />
the smolt can influence the mean lengths of the sea year classes . , is prov-<br />
ided by the figures of Table 33. When one examines the percentage share of<br />
des<br />
'the age groups in the sea year classes for every year4--8--met of smolt, one
Year's<br />
set<br />
1956 • A.1 +<br />
4 34 53 8<br />
1<br />
A.2 ±<br />
11 32 50 6<br />
1<br />
1957 A.1 +<br />
A.2 +<br />
1958 A.1 -I-<br />
A.2 +<br />
'At +<br />
• A.2 +<br />
3 24 64 8<br />
' 22 • 34 44<br />
1959 1<br />
1960 A.1 +<br />
A.2 ±<br />
•Avérage<br />
1956-1960<br />
A.1 +<br />
A.2 +<br />
- 174 —<br />
obtains the values in Table 46. It will be seen that the shares of the<br />
elass<br />
age groups of a yeal-4-s—ee4-of smolt change with increasing age.<br />
The percentages of the older fish (3.14 4,B and 5.B) become.<br />
.smaller at the rate at which the shares of the younger fish (1.B and 213)<br />
increase. These changes have no other explanation than that the older<br />
fish emigrate in order to spawn. That means that the sexual maturation<br />
is being determined not only through the duration of the<br />
but also through the duration of the stay in the rivers.<br />
not the du;s.tion of one of the two periods by itself is<br />
total age.<br />
stay in the sea,<br />
LP.333]<br />
In other words,<br />
decisive, but the<br />
Table X. The percentage composition of the sea year classes.<br />
Sea yeax Share of the age groups in the sea<br />
year classes in per cent<br />
class • 1.B 2.B 343 4•B 5.B<br />
4 31 46 17<br />
10 34 41 14<br />
30 51 11<br />
13 34 45 8<br />
5 26 52 15<br />
10 42 43 5<br />
5 29 53 12<br />
13 35 45 7<br />
• At other places it has been pointed out repeatedly' that the<br />
'emigration is connected with the size of the salmon (3.2.3). Applied to<br />
the above statement, this does mean nothing else but that within a sea<br />
,.year class and within its age groups the larger fish mature earlier.<br />
It is therefore possible that the statements about the existing stock are<br />
'correct when calculating the mean lengths. The rates of growth that have<br />
2<br />
1 '<br />
1<br />
2<br />
1
- 175 -<br />
• been ascertained from them are dependent on the number of the emigrated<br />
salmon and may perhaps be greater than stated. Finally, it is very probable<br />
that thè differences in the mean lengths that have been ascertained for<br />
the age groups of a sea year class would be greater when the emigrated<br />
salmon have been taken into account. This could have the consequence that<br />
the statistical treatment of the differences yields significant differences.<br />
The possibility is therefore not to be rejected that the size of the smet may<br />
influence thé length of the salmon in the sea.<br />
6. The food of the salmon of<br />
the Bal tic Sea<br />
The manner of life of the fish is determined in many respects.<br />
by their food.. Thus investigations of the food will suPply information<br />
about certain habits and behaviour. Furthermore, changes in the kind and<br />
, amount of the food consumed influence the composition of the tissues.<br />
Finally, the food forms an important component of the factors that deter-<br />
mine the growth.<br />
• 6.1. Previous investigations<br />
The differences between the life of the salmon in the rivers<br />
and in the sea have also affected the food investigations'. It is easier<br />
[P. 334]<br />
to obtain the material for investigation in the rivers than in the sea.<br />
There are therefore few papers that treat the nourishment of the adult<br />
salmon. •<br />
.6.1.1. The nutrition of the juvenile stages<br />
The nutrition of the salmonids in fresh water has been investigated
•<br />
- 176-<br />
since the turn of the century by numerous researchers. Statements about<br />
the first food of the fry after the yolk sack has'been consumed are, how.-<br />
ever, scarcet.'<br />
Th. Schrader (1928) has inveStigated specimens of Salmo trutta<br />
fario, about 20 mm long and found that they had eaten hardly any plankton<br />
crustaceans, but Mainly bottom crustaceans (Alona), in part also oligo-.<br />
chaetes. In Cumberland, Nova Scotia and New Brunswick H. C. White (1937)<br />
discovered larvae of chironomids in the stomachs of freshly hatched salmon<br />
alevins. A. Mitans (1963) has observed in subsequent years in the Salatza<br />
(Latvia) salmon fry of 38 mm length..In June the fish had eaten chironomid<br />
larvae that were numerically preponderant (100 to 200), but which amounted<br />
to only 21 per cent by weight, whereas Baetis (Ephemeroptera) represented<br />
50 pér cent. Ephemerella ignita occupied with 16 per cent by weight the<br />
third place. •<br />
. 'Fingerlings examined by White contained nymphs of ephèmerids<br />
in summer and in the fall mainly trichopterous larvae. In the older parr<br />
plecoptera play a role in winter, in the spring also Baetis . and EPhemerella,<br />
. as well as trichopterous laxvae.(A. Fritsch 1893, A. Mitans 1963). In his<br />
three-year investiations (1916 to 1918) G. Alm (1919) obtained similar<br />
results. Trichoptera (Hvdropsvche, Philipotamus, Rhvacophila) played the .<br />
important role.for paxr from April to November. Baetis was represented<br />
most<br />
almost.as well and unifotmly. The ptoportions of the other.animals flue-<br />
tuated during the course of the year. In.third place.were larvae of chir-<br />
onomids in May, in July/August imagos of insects, in October/November<br />
.plecoptera, and in April even Asellus.<br />
Caxpenter . (1940) thiffics that the kind of food consleed . depends<br />
on its availability. There is no loss of appetite, only lack of opportunity
(after K. A. Pyefinch 1955).<br />
— 177 —<br />
The largely similar results of the investigations indicate that<br />
there are only slight fluctuations in the basic food of juvenile salmon<br />
in the rivers. This statement conforms to the scientific opinion that there<br />
are hardly any fluctuations in the total productivity of insects, because<br />
the niche occupied by a weakly represented species is promptly filled by<br />
another.<br />
N. C. Morgan and A. B. Waddell (1961) collected the insects<br />
occurring in a trout lake with a floating trap and found differences in<br />
the catches of the same taxonomic groups from year to year that amounted<br />
up to the six-fdld. In contrast to the scientific opinion it was found,<br />
however, that the catch in 1956 was substantially better than that in 1955<br />
and in 1957.• The period of the main emergence of the insects extended from .<br />
April to September. Correspending to this, the salmonids ate during the<br />
winter at the bottom Gammarus, Asellus, Limnea, in the spring they ate<br />
mainly larvae of chironomids and and in late summer they lived on flying<br />
insects.<br />
6,1.2. The food in the main basin of the Baltic Sea<br />
For a long time there was no information available about the .<br />
food of the salmon in the sea, because material for investigation was dif-<br />
ficult to Obtain. Thus L. Roule (aecording to H. Henking 1929) was still<br />
of. the opinion that the salmon would seek out the depths of the sea after •<br />
.their émigration from.the rivers and feed on the large supplies of •<br />
benthic animals of the Atlantic shelf.<br />
It is probable that the first investigations of the food of sal-. .<br />
hai 335]<br />
'mon that had ben caught in the Baltic Sea along the coast of' Pomerania
- 178-<br />
were published by Eichelbaiim (1916). The results of his investigations •<br />
are. ?till of importance today, because he reports about the nutrition<br />
of the salmon during their first year in the sea. Twenty-nine emigrating<br />
smolt (14 to 27 cm) had lived from March till May principally on flying<br />
insects (Coleoptera, Diptera), besides on larvae of chironomids and gam-<br />
marids and isopods. Another 22 amolt of a length of 14 to 21 cm that had<br />
been caught in the sea .hetween May and October also contained Coleoptera,<br />
Diptera and gammarids. Of exceptional importance is, however, the finding<br />
that they had eaten in paxt'also Ammodytes. Some larger fish of a length -<br />
of between 36 and 60 cm, mostly, however, 41 to 51 cm long, were caught<br />
in March and April. Among the fish With stomach contents, 53 per cent had<br />
eaten preponderantly Ammodytes, 24 per cent had eaten mainly Gammarus and<br />
23 per cent had eaten Ammodytes as well as clupeids. •<br />
Similar investigations have been carried out by Henking (1931)<br />
on 134 salmon that had also been caught from 1914 to 1920 at the coast of<br />
farther Pomerania..During the months of February to May no decisive changes •<br />
were observed. In seven smolt of a length of 12 to 18 cm only flying in.,<br />
. sects were found. Of the remaining 127 salmon (36 to 52 cm length) more<br />
than 50 per cent had eaten Ammodytes (on an average 1.9 fish), 30 per cent<br />
contained Gammarus (1.9 specimen), 24 per cent had remainS of fish, mostly<br />
clupeids. Occasionally isopods and Crangon were found.<br />
The latest investigations of the stomach contents of smolts in<br />
-the Baltic Sea have . been made by Lindroth (1961b). The fish of a length<br />
of 13 to 22 cm were caught from June to August along the Swedish oixIst in<br />
the Bottensee. Almost all fish had eaten flying insects (300 to 500). One<br />
gmolt, 20 cm long, contained a fish.<br />
B. Dixon found in small'Eetic Sea salmon (mielnica) Ammodytes,
•<br />
gadids and sticklebacks (after K. Bahr 1936b).<br />
- 179 -<br />
K. Bahr (1935b, 1936b) was -the first to report on the stomach<br />
«content of large salmon in the sea: Among the fish investigated'were 139<br />
salMon of lengths between 73 and 116 cm. He was able to demonstrate that<br />
the changes in the composition of the food are related in the main to the<br />
seasonal vertical movements of the sand eel and of the sprat. During Jan-<br />
uary apd February the always pelagic stickleback was preponderant. With<br />
the warming up of the surface water , sand . eel and sprat moved up into the<br />
higher layers of water so that they can be captured by the salmon. Numers<br />
ically the stickleback was most common and was also most often eaten by<br />
the salmon.<br />
This result that is very impressive on account of the causal<br />
information, can, however, not be generalized and is not valid for all<br />
fishing grounds in the Baltic Sea, as could be demonstrated by Christensen<br />
(1961b) on hand of the hitherto most comprehensive material.(2100 salmon).<br />
In general the sprat must probably considered to be the most important item<br />
in the food during the entire year. They are followed by herring and stick,<br />
leback. The sand eel is of greater importance only to the south and south-<br />
east of Bornholm.'Netted salmon had larger stomach contents than the fish<br />
caught,on hooks. He did not find any food differences dependent on size .<br />
among the salmon of 60-cm to 95-cm length.<br />
F. Chrzan. (1960) has examined 65 netted salmon in the spring of<br />
1959 and 118 hooked salmon in the fall/winter of 1959 /60 from the Bay of<br />
Danzig. He came to the conclusion that the clupeids are the Most important<br />
food of the Salmon in every case. He thinks, however, that the herring<br />
. might play a more important.role than the sprat. Trigger fish and sand .<br />
eels follov behind the clupeids in regard to weight.<br />
•
6.2. Amount and kind of food according to my own<br />
investigations 1957 to 19 6 4<br />
- 180 -<br />
' The present investigations were carried out between 1957 and<br />
1964 on 2400 salmon (Table 47). More than one-half of the stomachs have<br />
been analysed on'land in the laboratory. For the collection of the mat-<br />
erial several salmon cutters were supplied with plastic pails that held<br />
about 70 to'80 stomachs each. After gutting, the fishermen put the entire<br />
intestines in formaldehyde on board. In this way it was possible to det-<br />
ermine also the sex of the fish. No exact statements of length could be<br />
obtained. Instead the length of the stomach was measured. The comparison<br />
Table 47. Number of salmon investigated and their<br />
times of capture<br />
Month Time of capture<br />
1957/8 '1958/9 1959/60 1961/2 1962/3 1963/4<br />
September .<br />
25 23<br />
Oktober - 91 71 66<br />
November • •<br />
221 151 .<br />
Dezember 122 151 .<br />
Janua'r 156 71 54<br />
Februar<br />
36<br />
Mârz •<br />
. 210 . 77 280<br />
April . 157 71 159<br />
. • Mai<br />
151<br />
•<br />
Juni 63 .<br />
•of the frequency distribution of these values with the series of measure-<br />
ments of coMplete catches df'salmon (Fig. 54) shows that a stomach length<br />
of 10 cm corresponds about to a tdtal length of fish of 66 cm and each<br />
further cm to a body length of 2.5 cm.<br />
In every case thé totarweight of the stomach content was as-<br />
certained first and then the weight and number of the individual prey.<br />
It 'was in general possible to identify food items that.had been strongly<br />
. digested with the aid of ooliths or by counts of vertebrae. That.was<br />
• •<br />
•<br />
[p. 336]
- 181 -<br />
especially decisive in, the „separation of clupeids into sprat and herring.<br />
Nevertheless, there remained a small percentage Of clupeids that could not<br />
. be identified and a further part of fish that could. no longer be determined..<br />
.<br />
The former have been assigned to sprat and herring according to the shares<br />
of these two species that had already been ascertained.<br />
In the investigations of food at sea ia was only possible to<br />
count and measure the prey. These figures have later been recalculated into<br />
weightS with the 'aid of the relations that had been established in the lab-<br />
oratory. •<br />
Of the 2406 stomachs of salmon that have been examined,1198<br />
49.8 per cent contained food with a total weight of 36,139 g. Of this 1416 g<br />
consisted of a slimy food mash. The remaining food constituents have been<br />
listed in Table 48. They amountto 34,723 g. Notwithstanding the rather<br />
long list of foo&constituents it is seen that only five specieS of fish<br />
and one crustacean species are of decisive importance. The clupeidP,<br />
especially the sprat, alone made up over 88 per cent of the food,weight,<br />
The sprat was found in 60 per cent of all .salmon that had taken food and<br />
herring in 20 per cent. Besides these two species of fish should be men-<br />
tioned in the order . of their .importance, (2.8 per cent of the<br />
food weight), Ammodytes (2.6 per cent), and stickleback (Gasterosteus,<br />
0.9 per cent). These fish Were found in 5 to 10 per cent of all salmon<br />
that had food in their stomachs. As a last group of importance have to be<br />
mentioned the mYsids, which made up 2 per cent of the weight and had been<br />
eaten by 9 per cent of the salmon.<br />
[1" 337]<br />
Cod, amphipods and Crangon were present in 1 per cent of the<br />
salmon. With the exception of the cod they do nàt play any role, in regard<br />
• to Weight, «nor as to the number of individuals (Table 48).
Table 48. Constituents of the food of salmon<br />
1957-9 and 19 6 1-4.-<br />
Weight Number of sal-<br />
Prey . g per cent mon with the Number<br />
Total 36,139 particular of<br />
Nash 1,41 6 food in rare<br />
per cent prey<br />
"Remainder" 34,723 100.00<br />
Sprattus sprattus 75,51 60<br />
Clupea harengus ' 13,00 20<br />
Belone belone 2,82 8<br />
Ammodytes Spec. 2,56 5<br />
Mysideae 1,96 9<br />
Gadus morrhua 1,79 1 27<br />
Gasterosteus • 0,94 9<br />
Scomber . 0,24 1<br />
Merlangius merlangùs 0,16 -3<br />
Onos spec. 0,08 2<br />
Alosa fallax 0,06 ' 1<br />
.<br />
Amphipod.<br />
0,04 1<br />
Crangon 0,03 1 13<br />
Cottus spec. 0,03 1<br />
Rutilus 0,03 2<br />
Sonseige Fische, Grâten OTHER FISH • 0,75 1<br />
Corixa ' BONES < 0,01 1<br />
DytisCuS < 0,01 1<br />
Luflinsekten flying insects < 0,01 1<br />
Tunikat tunicates
6.3.1. Seasonal fluctuations<br />
36,9<br />
26,1<br />
13,2<br />
12,1<br />
16,9<br />
16,5<br />
10,1<br />
37,5<br />
61,1<br />
36,5<br />
30,3<br />
26,7<br />
70,3<br />
27,7<br />
24,9<br />
10,4<br />
46,5<br />
35,1<br />
61,8<br />
39,5<br />
- 183-<br />
In the treatment of the growth it haF been shown that growth<br />
is Very rapid during the summer months and that it is slower in winter.<br />
Furthermore, there is a loss of condition in the cold season (Fig. 57).<br />
[P. 33 8 ]<br />
These phenomena Can have two causes, the different speed of digestion in<br />
dependence on the temperature and changes in the availability of the food.<br />
If temperature were the only effective component then we could expect the<br />
sanie average condition in winter as well as in summer. If the filling of<br />
the stomach is reduced during the winter with simultaneous deterioration<br />
in condition one can refer -this to the salmon having at their disposal'<br />
less food in the cold season than in summer.<br />
Table 49. Monthly changes of the food weight per salmon in g,<br />
mean of the years 1957 to 59, 1961 to 64, line and net catches.<br />
Mean food weight per salmon in g<br />
Mean<br />
Month<br />
1957-9, 19 6 1-4 0.<br />
'Mean<br />
Christensen<br />
of all -Mean of salmon<br />
(1961)<br />
salmon ' with food<br />
1960/1<br />
September 36,9<br />
Oktober 15,6<br />
Novernber 4,5<br />
Dezem.ber 7,2<br />
Janùar 7,2<br />
Februar. 11,9'<br />
Mârz<br />
April 26,5<br />
Mai 59,0<br />
juni 34,8<br />
Weighted mean 15,1<br />
Simple mean 21,0<br />
In order to test this question it must be established how the<br />
average weight of the stomach content changes from month to month. Here<br />
we meet a difficulty. It has already been said that about one half of the<br />
stomachs.examined did no longer contain formed food or were empty. In
- 184 -<br />
Table 49 have therefore been given two figures for every month. The mean<br />
weight of food has been calculated first for the total number of all sal-<br />
mon examined and second only for those fish who had a full stomach.<br />
Botk figures show that the weight of the stomach content is<br />
highest in fall and spring and_lowest during the winter months, especially<br />
from November to March. The investigations of Christensen (1961b) show a •<br />
similar result. It is therefore probable that the food supply of the sal-<br />
mon is smaller in the winter than in summer. On account of the cessation<br />
.of the salmon fishery in summer, we could obtain no samples in July and<br />
August. One can, however, assume that the values for these months would<br />
not be substantially different from those for May/June.<br />
A comparison.with the results of Christensen shows a consider-<br />
..able difference in the amount of food. His values for the season 1960/61<br />
are on an average almost twice as large as the mean values of my material.<br />
Christensen has investigated fresh stomachs that had been collected on<br />
board and frozen, whereas my material had been preserved in formaldehyde.'<br />
It is, hOwever, quite obvious that the large differences cannot have been<br />
caused by different : methods of investigation, but must have thpir cause<br />
• in the better availability of the food in the season of 1960/61.<br />
ye- tin<br />
A glance at Fig. 36 shows that principally the yeeri-s-set of<br />
smolt of 1959 has profited'from the extraordinarily good food supply of<br />
the season of 1960/61. But also thé good growth of the year's sot of smolt<br />
of 1958 during the third year in the sea can be brought into agreement with<br />
this.<br />
$ince seasonal changes in the take-up of food are probable,<br />
we shall once more refer to the, fact that only about one-halUof the eal-<br />
.<br />
mon investigated had food in the stomach. Chrietensen has indicated that<br />
•<br />
LP. 339] .
•<br />
Number of Months<br />
Gear salmon<br />
investigated IX/X XI/XII I/II III/IV V/VI Total<br />
Line Total<br />
p.c. with food<br />
. _<br />
187 645 263 13 1108<br />
64 44 43 100 48<br />
Nets Total 89 54 941 214 1298<br />
p.c. with food 83 44 41 88 51<br />
Total p.c. with food 70 44 4 3 - 41 88 50<br />
--r<br />
- 185-<br />
the salmon, especially those caught on hooks, are perhaps inclined to<br />
vomit the food in their stomachs. On the other hand, it is possible that<br />
more salmon with empty stomachs are found in winter than in summer, so that<br />
this phenomenon could be explained, at least in part, by the smaller avail-<br />
abillty of the food. In this connection let us examine the percentages of<br />
salmon With full stomachs in Table 50. Between November to March or April,<br />
.respectively,only<br />
, about 43 per cent of all salmon .have food in the stomach,.<br />
60<br />
40<br />
20<br />
Table 50. Seasonal changes in ratio of salmon with empty<br />
stomachs to those with full stomachs.<br />
9 ,4.9...0.0 Stomach contents<br />
G0110 ,10<br />
Ooozg. fol Danzig Deep<br />
0 0 0011004<br />
Fig. 39. Mean weight of food per salmon in g on the<br />
fishing grounds 5 and 6, 1957 - 9 and 19 6 1-4.<br />
mc,,e.- IMemths
•<br />
- 186-<br />
whereas the share was 70 per cent in September/October and even 88 pert<br />
cent in May/june. After this result we may ahmune that the share of sal-<br />
mon with empty stomachs gives an indication of the availability of food.<br />
Therefore all results will be correlated in the following investigation<br />
with the total number of the salmon examined.<br />
6.3.2. Différences on the fishing grounds •<br />
Since the size of the weight of the stomach contents depends<br />
on the season, only such data can be used in the compaxison of different<br />
fishing grounds that take such facts into account. The data on hand orig-<br />
inate frOm the fishing grounds 4, ,5 and 6. From the fishing ground 4 data<br />
are available only for the months September (1962, 1963) and October (19 6 1,<br />
1963). Data from the other two fishing grounds are very scarce as fax as<br />
they apply to the same months* and fishing periods. For this reason means<br />
[p. 340•<br />
have been'calculated froM the values of all years and their seasonal course<br />
is given in Fig. 39. The values from the fishing grounds 5 and 6 show good<br />
agreement from December to April. In contrast, the salmon-had in October<br />
1957 near Bornholm more than twice the amount of food in their stomachs<br />
than had the fish'of the Danzig Deep. The values for October from the fishing<br />
ground 4 (Gotland) agree.well.with thoEe from Bornholm.<br />
• AlthoUgh it is not possible to obtain differences in the food<br />
weight of a salmon that are unambiguously dependent on the fishing ground,<br />
there are found certain variations in regard to the composition of the food<br />
on the individuar fishing grounds (Table 51).<br />
On.ths fishing ground 6 it is true that the sprat predominates<br />
in the food, but it is represented to a smiller extent than on the Danzig<br />
• Deep. It is also found that.Belone, Ammodvtes and even the mysids can form
MagerdW hing<br />
40<br />
, 20<br />
Filling of Stomach<br />
•---,0 nelzgetarigene Lochs, netted salmon<br />
ci—Cr geongelle (ochre hooked salmon<br />
•<br />
•<br />
•,'"<br />
XI XII IV monae•Months<br />
Fig. 40. Pbod weight of salmon, caught in the Danzig Deep<br />
with line and net.<br />
- 187 a -
- 187-<br />
important constituents of the food, whereas in the Danzig Deep only<br />
Belone played a temporary role.<br />
Table 51. The most important food ingredients as percentaes<br />
of the total food weight (without the unidentifiable mash).<br />
Fishing Months Mean<br />
Food . value<br />
ground IX X XI XII I II III IV V VI simp. weig'd<br />
5<br />
Sprattus<br />
Clup. har.<br />
Belone<br />
Ammodyt.<br />
Gasterost.<br />
Mysideae •<br />
57 67 45 36<br />
10 20 31 29<br />
29 9 16<br />
2 4 11<br />
0 2 8 1<br />
0 0<br />
5 90 97 69 58 76<br />
80 7 2 31 26 14<br />
0 7 2<br />
1 I 1 3 • 1<br />
3 0 2 1<br />
8 0 1 0<br />
6<br />
'<br />
Sprattus<br />
Clup. har.<br />
Belone<br />
Ammodyt.<br />
Gasterost.<br />
Mysideae<br />
•<br />
75<br />
25<br />
8 79<br />
39 2<br />
38 19<br />
8 0<br />
0<br />
54 25<br />
7 11 0<br />
1<br />
73<br />
1 1<br />
91 33<br />
40 29<br />
14 16<br />
IO 16<br />
12 15<br />
2 3<br />
21 18<br />
4<br />
Sprattus<br />
Chip. har.<br />
Ammodyt.<br />
Gasterost.<br />
89 96<br />
9 1<br />
1 2<br />
0<br />
93 93<br />
5 5<br />
2 2<br />
0 0<br />
0 = . .< 0.5 per cent<br />
6.3.3. Differences in dependence on the gear employed<br />
No exact comparison is possible between the weight of the<br />
stomach content of salmon caught with line and that of salmon caught in<br />
nets. There are no data for both kinds of gear corresponding to the same<br />
months and years and the same fiehing grounds. In Fig. 40 have therefore<br />
been inserted the mean value s . for the years of investigation on the fishing<br />
ground 5 (Danzig Deep). According to the curve there are apparent no sub-<br />
stantial differences from October to March. Only beginning in April do the<br />
netted aalmon show a considerably-larger stomach content than the hooked<br />
salmon. However, this result has to be accepted with reservations, because<br />
in March only five and in April only eight" hooked salmon from the Danzig<br />
LID. 341]
Deep could be examined.<br />
- 188 -<br />
Christensen (1961b) had a more extensive material at his dis-<br />
position. He examined in October 1960 the stomachs of 147 netted and 192<br />
hooked salmon and in January 1961 thOse of a further 147 netted and 229<br />
hooked salMon. He came to the conclusion that netted salmon contain con-<br />
siderably more food than hooked salmon. The figures were for the northern .<br />
Baltic Sea 50.4.g (netted) and 27.8 g (hooked), for the eastern coast they<br />
were 34.3 and 15.1 g, and for the Bay of Danzig they were 12.8 g and 9.4 g.<br />
9ear<br />
Table 52. Weight of food and proportion of clupeids in<br />
male and female salmon.<br />
Number of salmon Weight of food per salmon<br />
examind in g<br />
Total Clupeids<br />
9 d 9 d 9<br />
. .<br />
Net 334 235 23,2 24,2 20,3 22,4<br />
Linp 204 150 12,4 13,0 10,0 9,6<br />
_<br />
Total 538 385 19,1 19,8 16,4 17,4<br />
6.34. Differences depending on sex<br />
-During. the examination of the stomachs in the laboratory, ït<br />
was always possible to determine the sex of the salmon. The results, as<br />
fax as they concern - the total weight of the food and the proportion of<br />
clupeids, have been assembled in Table 52.<br />
DifferenCes in the amounts of étomach content of -nettedand<br />
hooked salmon can be referred to the months of capture. In regard to the<br />
sexes it is found that thé males show a slightly higher weight of food<br />
than the fémalea. The differences are not.significant.<br />
• 342]
•<br />
6.3.5. Differences in food related to the size of the salmon<br />
Christensen (1961b) did not find a connection between the kind<br />
of food And the size of the salmon when he examined his fish that had<br />
a length of 60 to 95 cm. Neither did he find that the larger salmon had<br />
more food in their stoamchs. He explains the latter by the larger surface<br />
of the stomachs in.the large salmon and the consequently more rapid diges-<br />
tion. The preeent investigations also show no size-dependent differences<br />
in the salmon with lengths from 60 cm to 112 cm.<br />
Table 53. Fàod of smolt and post-smolt according to different<br />
authors (percentage of salmon with food in stomach<br />
in parantheses).<br />
Author Months<br />
Fish. Am- Fly-<br />
Num- L Clup. Amm. Bel. phi- ing<br />
ground ber cm pods ins.<br />
-<br />
-<br />
EICHELBAUM V-X Pomm. Kiiste 22 14-21 + ' + +<br />
HENKING IV-V Kolberg 7 12-18 LI-<br />
LINOROTH VI-IX Bottensee 46 13-22 + +<br />
HENKING II-V Kolberg 127 36-52 -I- (24) 1,9 (50) 1,9 (30)<br />
THUROW XI-IV Danz. Tief 6 28-48 • 2,7 (100) 0,2 (17)<br />
[Pomm. Kiiste = Pomeranian coast, Danz. Tief = Danzig Deep]<br />
The food of the smaller salmon (A.1), which in general are not<br />
yet exploited, is of greater interest. Only six specimen with a length of<br />
from 28 to 48 cm could be.examined. The results have been summariied iri<br />
Table 53, together with the results of other authors. As has already been<br />
stated, thé Smolt in the Balt4o eat to begin with mostly flying insects.<br />
Some fiéh, however, change very soon to a diet of fish. Lindroth fOund a<br />
fish in à emolt of a length of 20 cm and Eichelbaum could_demonstrate Am-<br />
màdytes already in smolt.with a length of 14 to 21 . cm. When they are over<br />
. 30 cm long.one . finds predominantly fish as food.<br />
One can reckon that the rapid growth begins only when the young<br />
- 189<br />
-
- 190 -<br />
salmon . switch over to the compact food of crustaceans and fish. This doesnot<br />
man H that crustaceans and fish do predominate in the food only after the:fish<br />
have reached a length of 30 or 40 cm, but that they are decisively respon-<br />
sible for the attainment of this size and are therefore eaten alreaey<br />
earlier in greater amounts. One can deduce furthermore from this finding<br />
that the final growth performance of the salmon is dependent to the largest<br />
extent on the moment when the post-smolt switch to fish food.<br />
6.4. The relation between the behaviour of the prey and the composition<br />
. of the food of the salmon<br />
CobOrSe<br />
Ut)<br />
• (On hand)of the food investigation could be established that in<br />
the Danzig Deep the proportion of sprat is smallest from December to March,<br />
whereas the proportion of herring increases simultaneously. This finding<br />
agrees with the yields. The greatest catches of sprat are being madeduring<br />
the time of spawning (May/June) and the best catches of herring are during<br />
spring and fall (FL Berner 1963). The sprat make daily vertical movements<br />
during the warm season and feed., at night on plankton in the upper layers<br />
of water. In contrast,-they remain in winter principally in the layers near<br />
the bottom (E. Ehrenbaum 1936, K. Bahr 1936b). Only amall amounts of sprat<br />
were caught from 1953to.1960 to the southeast of Bornholm. The catches<br />
in the Bornholm Basin were also relatively mall. This fact coincides with<br />
the amall importance that the sprat has as food for salmon on the fishing<br />
ground 5. In all'areas of the central and southeastern Baltic Sea, the<br />
best catches of sprat per unit effort are made in May to lugust, with<br />
maximum values in June and July (M. Berner 1965e J. Elwertowski 1959).<br />
Belona and sand eel stay during the summer in the ûpper water<br />
layers in order to eat plankton. Some individuals, however, carry out<br />
[P. 343]
•<br />
- 191 -<br />
vertical movements also in winter. The share of these kinds of fish . there-<br />
fore changes often in the opposite direction from that of the sprat.<br />
Belone and sand eel become more conspicuous only when the clupeids.beoote<br />
scarcer.<br />
6.5. The food consumption of the salmon<br />
For the treatment of this question we have only the mean weight<br />
of food, which was, according to Table 49, at its lowest during the six<br />
months October . to March. For this period we obtain as the simple mean a<br />
value of 8.7 g stomach content. The corresponding amount for the remaining «<br />
four months amounts to 39.3 g. If we assume that the latter value applies<br />
also to the months July and August, for which there is no informatiOn, •<br />
then the annual mean for the weight of food is 24 g.<br />
In the literature available to me (W. O. Côrnelius 1933, H. Mann<br />
1955, M. E. Brown 1957, various authors after E. J. W. Barrington 1957)<br />
are few statements about . the'frequency of food intake in fish and none for<br />
the salmon.-<br />
According to. Barrington (1957) the speed of digestion is smaller<br />
in fish than in memals on account of the lower temperature. At 10 ° C the<br />
.food passes through the - carp in 181Tr, at 26 ° C it does so in 4.5 hr. In<br />
sharks the digestion is supposed to be complete after three days. Karpevich<br />
and Bokova (after Suvorov 1959) state for cod and sea scorpion that the<br />
skin.of fOod fish.that is in contact with the walls of the stomach is in<br />
part dissolved after 5 hr. Cornelius (1933) fed-fingerlings of the , rainbow<br />
trout.With trout fry. He found the first indications of digestion on skin<br />
and fins of 'the fOod . fish. After five hours fins, skin and eyes were decom-<br />
•posed and the body.càvity had.been opened. The body shape was no longer
•<br />
- 192 -<br />
recognizable after seven hours, although the flesh was still adhering to<br />
the vertebral column. After twelve hours it was no longer possible to<br />
recognize remains of the food.<br />
When investigating the digestive processes in various freshwater<br />
fish, Mann (1935) could demonstrate that the speed of digestion depends<br />
on different factors. Among other things, the age of the fish, the tem7<br />
kind and amount of the food taken up play a certain role.<br />
perature and the<br />
Large pieces of food', the surface of which is relatively small, require<br />
h. 344],<br />
a longer time for digestion then do small pieces of food.<br />
The salmon examined in this work are fish that have been cap-<br />
tured during the night or towards môrning and that were gutted generally<br />
towards noon, frequently also already during the forenoon. The pieces of<br />
Belone and the sprat that have been used as bait can be identified unam,<br />
biguously as such; the former because they had been cut into pieces and<br />
the latter because the head . had been damaged by the hook. The bait may<br />
have been exposed to the digestive juices for about two to ten hours<br />
before gutting. Nevertheless, no instances of considerable damage-by the<br />
digestive juicesieceObserved. During the time of investigation the tern!,<br />
perature was seldem higher than 12 ° C.<br />
For a start, let us assume that the salmon takes daily the<br />
amount of food of 24 g that has been cited above. That would amount to a .<br />
yearly total of 8760 g. This amount'cannot be considered to be sufficient<br />
for the metabolism of the salmon. According to Table 43 the increase from<br />
the age group A.1+ to A.2+ amounts to about 4000 g. It can hardly be im-<br />
agined that the salmon should not require.more food than 8760 g for met-<br />
abolism and for the synthepis of 4000 g body substances. The amount of<br />
food actuaily-consumed was probably greater. Let us therefore attempt<br />
•
to discover the annual food intake in a different manner.<br />
- 193 -<br />
M. Brown (1937) found that Salmo trutta of a weight of 100 g<br />
or over at a temperature of 11.5 ° C required a constant'supply of energy<br />
equivalent to about 60 mg fleshier fish and week. The conversion factor<br />
for anabolism at 11.5 ° C was 4.5. In addition to the food for the energy<br />
supply, the fish had to take up 4.5 food flesh in order -to grow by one<br />
gramme of weight. No indications about the energy requirements of large<br />
fish have been given. We may, however, assume that it will rather diminish<br />
with increasing size of the fish than increase. E. Halsband (1953) estab-<br />
lished that the - energy'requirements of rainbow trout are smaller in salt-<br />
water than in fresh-water. Let u s . use the values cited for the calculation<br />
of the food intake of a salmon of the age group A.1+ for one year. That<br />
can give us an idea of the.order of magnitude of the metabolism.Ye obtain<br />
then for the energy supPly (sustaining food) 15,600 g and for the weight<br />
increase of 4000 g food for anabolism in the amount of 18,000 g. Within<br />
52 weeks there is thus required a total of 33,600 g. That corresponds to .<br />
food coefficient of 8.4 (8.4. g food for 1 g increase). Brown (1957)<br />
. cites for brooktrout (Salmo trutta) the food coefficients established bY<br />
different authors as 2.3 to 7.1, whereby .different kinds of food were<br />
being.used as bases. According.to this comparison the figure of 8.4 for<br />
the 'salmon that we just calculated gppears to lie entirely in the limits of<br />
the possible. The average daily food intake Of à salmon in the second year<br />
in the sea would then amount to about - 92 g.<br />
When comparing this figure with that given above of 24 g, one -<br />
has to.consider that surely some salmon.had already,been caught before<br />
they'had the opportuniy !to feed. Probably only few fish have,been cap-.<br />
tured that at the time Of capturé had already taken up -the potential ..<br />
a
- 194 -<br />
amount of food. Under-consideration of the assumption that the requirement<br />
for energy that has been taken as basis may represent a maximum value one<br />
has to view the weight of 92 g as the average maximum amount of the daily<br />
food intake, whereas 24 g represent a minimum value.<br />
-The number of the Baltic Sea salmon in the exploited stock is<br />
estimated on an average for the years 1956 to 1963 as 10 6 . These fish have<br />
taken up as food about 15,000 tà 30,000 t according to the above figures.<br />
[p. 345]<br />
Of this the sprat accounted for about 10,000 to 20,000 t. The total yields<br />
of this fish as the mean for the years 1956 to 1960 amounted to 26,000 t<br />
(Bull. Statistique). According to this the sprat consumed by the salmon<br />
may.be estimated to have amounted to about 50 per cent of the total amount<br />
that the fisherMen have marketed from the entire Baltic Sea.<br />
7 . Attempt at a quantitative<br />
anal.ysis of the stock in the main<br />
basin bf the Baltic Sea<br />
. In the treatment of biological questions the individual has<br />
been the main object of investigation for a long period. It has been con- ,<br />
• sidered as rePresentative of the species in every respect. With the appear<br />
ance of new goals for the work, groups of individual, the communities of<br />
life, moved into the roreground. Not the individual being, but the effecté<br />
of the vital processes of à number of individuals occupied the centre of<br />
consideration. This method has long-played abonsiderkiàs.±ole 111f4hery<br />
ogy asthe study of the stock.<br />
A stock is, howeVer, not a static, but a eynamic unit and the<br />
investigation of it is more of actual valuethan of a historical one. - . The<br />
supervision of' the Conditions of the stock has thereftre to he continuous,<br />
so the it will«be possible to recognize changes and to connect thèm witb
•<br />
- 195 -<br />
external factors.. The investigations of fish populations that are being<br />
carried out at present have the object to oaic the fundamentals for a<br />
planned fishery -. It has to be discovered by what amounts the stock in.-<br />
creases and diminishes annually and to what extent these processes can<br />
be influenced by man. It is of special interest to learn in what manner<br />
can be obtained the best yield without impairing reproduction.<br />
7.1. The characteristics of the stock<br />
• Before one can begin to investigate the conditions in a stock,<br />
to ascertain their changes and the cause:, of these changes, it will be<br />
necessary to define thé stock. However, one can consider one fish popul-<br />
ation to be separate from another only then; when there are criteria in<br />
regard to which the two differ.<br />
• The first question, therefore,'is: what is a stock? A. Bdckmann<br />
(1929) saw'the problem in its widest sense and considered the stock tO be<br />
a unit in regard.to migration, the phenomena of growth and maturation,<br />
as well as the phenomena Of reproduction and waste. Among others, it is<br />
possible to make a demarcation by means of labelling or investigation of<br />
races..Parrish and' Sherman (after Hempel and :ahrhage 1961) designate stocks<br />
of fish as biological fundamental groups, into which the population can be<br />
divided in order to obtain independent units that can be influenced (by<br />
man). According to Hempel- and Sahrhage (19 6 1) the stock of fish is an<br />
independent unit that is closed in itself. The stock Consists of a reprod-<br />
uctive community that is self perpetuing, the - independence of which is<br />
guaranteed.through geographical isolation or reproductive barriers.<br />
Furthermore,. five criteria are named (N. N. 1962), boundaries<br />
of distribution; spawning areas, uniformity of the values of fishing and<br />
r
- 196-<br />
expenditure, composition in regard to age, and morphological, as well as<br />
physiological characters that serve to define a stock. The last definitions<br />
have been offered in connection with population-dynamical investigations.<br />
For the quantitative consideration of a stock it is necessary to delimit<br />
•<br />
lp. 346 ]<br />
a stock less from a biological point of view than from the standpoint of<br />
fishery, in order to ensure that the figures of yield that are used as<br />
basis relate only to a definite population. •<br />
In the present chapter an attempt will be made to carry thropgh<br />
a quantitative, analysis of the stock. Let us assemble the . characters def-<br />
ining the stock that have been cited above and apply them to the salmon<br />
of the Baltic Sea.<br />
A.uniform.stock ("unit stock") inhabits an area that iS frequently<br />
. delimited tbpographically and propagates within this area of distribution.<br />
It can be fished in continuous isolation. Exchange with other populations<br />
has an insUbstantial.influence on the composition of the stock.<br />
If wa now consider the Baltic Sea salmon, we can state at the<br />
• outset that these fish are unambiguously confined in their distribution<br />
(see 4. migrations). The-western Baltic Sea with the Belts forms the western'<br />
boundary of distribution. An'exchange with other regions does praàtically.<br />
not ciecur. Within the area, however, quite a number of rivers are visited<br />
for spawning. This fact, however, does not justify to consider each river<br />
population(as . its own stock, 'because the spawning fish together with other<br />
individuals are- being exploited . in the Baltic Sea before their return . td<br />
. .theirivérs. In addition, several investigators could show that the great<br />
changes:that occur in ébe riverï oan be followed quite uniformly in all<br />
• the others .(G. Alm 1928a, 1928b, 1958; N. llagmann 1938; T. H. anti 1938,<br />
:1948;. Lindroth.1950, 1957; G. Svârdson 1957a).<br />
• -
7 197 `<br />
It has already bee/I .:stated -that the present investigations of<br />
the fishing intensity and the strength of the stock are based only on the<br />
salmon fishery in the main basin of the Baltic Sea. Therefore, we must<br />
restrict oursellies to a part of the stock on account of the limited.data.<br />
Slich' a delimitation can bè carried .out when one considers the immigration<br />
of the young salmon from the Gulf of Bothnia as recruitment and all losses<br />
except natural mortality and loases through fishing as spawning migration.<br />
The recruitment is taken care of through the divers values of the stock<br />
density. The figures that are obtained for the spawning migration com-<br />
prise all salMon that emigrate from the main basin. This part of the stock,<br />
however, becomes subject to shore and river fishery, so that only a certain<br />
percentage of the spawning migrants actually reaches the spawning grounds.<br />
These events, however, are of no interest to us, Since only an unimportant .<br />
fraction of Balm.= survives spawning and returns to the Baltic Sea, all<br />
spawning migrants are counted from the beginning as defdnite losses.<br />
7.2: Lbsses in the eXploited stock<br />
yew e.(a.ss<br />
In the above chapters it has been shown that a-ye-eta-es—set<br />
becomes eiploited for the first time during the fall of the second year<br />
in the Baltic Sea. One has therefore to distinguish between an undisturbed<br />
stage and an exploited phase. Since the fishing season commences in the<br />
fall of each year,.the - transition-between the two sections Occurs rather<br />
suddenly. During the first phase, losses are caused only by natural causes<br />
(enemies, sickness,lack of food), later the losses through fishing are<br />
added. Finally, a Part of the salmon migrate in order to spawn and<br />
- thus leave the exploited phase. At this time there are-three different<br />
causes that work logether_and lead to a reduction of the stock. The total'of
•<br />
- 1 98-<br />
the stock losses are composed of the waste by fishing, the natural mortal-<br />
ity and the losses caused by the spawning mration.<br />
7.2.1. Total mortality<br />
Beverton and Holt (1957) have, among other things, described<br />
the losses in a stock of fish with the aid of a differential equation.<br />
According to this the number of fish that is lost from the stock in the<br />
time t is proportional to the total mortality Z and the number N of the<br />
fish present.<br />
obtain<br />
dN =<br />
dt<br />
Through solving the differential quotient and integration we<br />
W<br />
- t<br />
W<br />
The mortality . thus follows the law of exponential dependence.<br />
N is proportional to t, when t increases arithmetically, N decreases geo-<br />
metrically. Z . is called the exponential coefficient of the total losses.<br />
Equation (1). thus gives the number of survivors at the time t.<br />
. The nuiber of the dead is then<br />
N o _ N t= N o _ oe -Zt<br />
.<br />
• N o -'r t D0 (1 e t)<br />
With the aid of - (1) and . the values available, one can now<br />
calculate the total mortality<br />
11- = 0. e<br />
ln 1.4 = Zt<br />
ln -D = Z:t N<br />
t<br />
(1 )<br />
(2)<br />
(3)<br />
[ p. 347]
•<br />
- 199 -<br />
For the calculation of Z from (3) no absolute numbers are<br />
required. It is only necessary to have the rat::.o of the strength of the<br />
. stock at the time 0 to the strength at time t. It is true that it is neces-<br />
sary to insert the figures for one feecel-s-set in consecutive years. How-<br />
etc el-,<br />
ever, such data are available, since in 2.3.3.2. we consider the e-aptu4te<br />
per unit effort as an expression for the strength of the stock. If we re-<br />
calculate these figures (Table 15).for the corresponding age composition<br />
in per cent (Table 33), we obtain then the figures in Table 54. These<br />
Values show the losses of a .4ici-4-se "s t during the course of two years<br />
(providing there are no errors in the determination of the age and in the<br />
eta,t-f-<br />
determination of the captures per unit effort). If we examine, e.g., the<br />
-y-ea-r-l-s---set-ef-smca-t of 1955, which was present in 1956/57 as the sea year<br />
class A.1+. Of this yeart 18.5 salmon pèr 1000 hooks were caught. In the<br />
following season it yielded as A.2+ only 4.1 salmon per 1000 hooks and an.-<br />
other year:later as A.3+ -e.o..e.* only 0.6 salmon. The total losses during the<br />
second year in the sea amounted thus to almost 78 pèr cent, in the third<br />
year in the sea, they were 85 per cent.<br />
nad,c ,;<br />
If we insert the cieturco per unit effort cited into (3), we .<br />
obtain as coefficient of the total mortality ln (18.5/4.1)= 1.51. For the<br />
fishing periods under'discussion the mean value of the . losses in the . second<br />
year Z 2 ,--. 1.23 and in the third year Z 3 . 2.20. That corresponds to per<br />
centages of 70.8 per cent and 88.9 Per cent, respectively: During the first<br />
year of exPloitation tiremmLsean average of 70.8 per cent are being<br />
sh,ou<br />
. removed from the new y.s.9,-PLe-eat through fishing and other causes. The<br />
losses suffered by the remaining fish amount in the second year of exploi-<br />
tation to 88.9 per cent. Of the salmonthat had entered originally into<br />
'the exploited phase only 3.2 per cent were left after two years. This
NUmber of salmon per Z Weigh-<br />
Season 1000 hooks ted<br />
Tot. A.1+ A.2+ A.3+ A.1+ A.2+ mean<br />
f +f<br />
f 13+1<br />
2<br />
- 200 -'<br />
result agrees.with.the findings that have been obtained on hand of the<br />
age analyses. Only the two sea year classes A.1+ and A.2+ play numerically<br />
any role in the stock of salmon in the Baltic Sea.<br />
LP. 54 8 1<br />
Christensen (1964) could base his investigations on the Danish<br />
s and German:expenditures.He found total losses of Z 2 = 1.33 and Z 3 = 2*.23<br />
that do not.deviate substantially from the above figures.<br />
The individual mortality values in Table 54 show considerable<br />
fluctuations. The value of Z = 0.05 as it has been obtained for the sea<br />
. year class A.1+ in the season 1957/58 cannot possibly be correct, consider-<br />
ing the recorded expenditure of f = 4.44 (Table 5). Let us therefore exam-<br />
ine once more the figures used as a basis. For the calculation of Z were<br />
Table 54. Values of the total mortality in Baltic Sea<br />
salmon .(by using the eartierrey lineyper unit effort).<br />
1956/57 24,0 18,5 . 5,1 0,4 1,51 2,14 1,61 4,91 4,68<br />
1957/58 10,5 5,7 4,1 . 0,6 0,05 1,92 0,36 4,44 3,96<br />
1958/59 22,5 16,2 • 0,6 1,42 3,30' 1,64 3,49 3,94<br />
1959/60. 8,4 4,1 3,9 0,3 0,58 1,47 0,92 4,38 4,56<br />
1960/61 10,8 8,3 2,3 0,9 1,78 2,44 1,89 4,74 5,16<br />
1961/62 15,8 14,3 1,4 0,2 2,02 1,95 2,01 5,57 5,43<br />
. 1962/63 8, 5,9 1,9 0,2 • 5,3 1<br />
Mittel Me an 1,227 2,203 1,41<br />
1 On account of the ice conditions the effective expenditure<br />
Was only 3.62 in 6 months. For 8.8 months we assume here<br />
f = 5.3, because the vessels of other countries could carry<br />
on fishing to the full eXtent.<br />
used the percentages of the age composition as well as the data of Sle<br />
eedei-ree- per unit effort. In regard to the age composition it has already<br />
been established that the results of the present analyse s . correspond rather<br />
well with the actual . conditions. Let us therefore examine what effect is<br />
due to the changes in the eeptures per unit effort. ldhe4 the value of the
- 20 1 -<br />
ceptu.ye per unit effort of 1957/58 increaes bs ten per cent, then Z2 rises<br />
from 0.05 to 0.15. Increases in the capttbre.pr unit effort by 20, 30, 40<br />
per cent result in corresponding values of Z. ) of .0.23, 0.31, 0.39. Even<br />
this amount must be considered as too small. Un the other hand, we cannot<br />
Cc<br />
assume that the -e-sekttte,e per unit effort in 1957/58 should have amounted<br />
to- mere than 14.7 instead of 10.5. It is, however, also possible that not<br />
only the value for 1957/58, but also that for the following season is<br />
affected . by errors. gowever, if both data are changc-sd then we find consid-<br />
erable effects on the results of the -iirculations for the neXt fishing<br />
season. After it has been shown (2.3.3.2.) that the -captures per unit ef-<br />
fart are subject to other influences than that of the itrength of the stock,<br />
and that these influenees cannot be eliminated readily, one has to reckon<br />
after all with certain effects on the calculations of the mortality.<br />
There is still another problem to be considered. The data for<br />
the present estimates are based on the yield of the German salmon fishery<br />
that amounts to only 15 per cent of the total. Changes that were caused<br />
by the efforts of other fleets cannot be expressed in the present data. We<br />
have therefor e . to reckon with incorrect individual values under certain<br />
circumstances.<br />
• The figures for Z that have been obtained with the aid of the<br />
captures by net per unit effort (Table 55) change little. The average<br />
values for Z 2 are slightly smaller; theSe for Z 3 are slightly greater<br />
than. those in Table 54.<br />
[P. 349]<br />
For the determination of the total mortality .can also be used<br />
the method of the virtual population. The virtual population of a certain<br />
V 'Ye '>‘<br />
Yt‘raer4-7--Set is the total ntimber of all captured fish of this ydrarle sct.<br />
The mortality in the year x + 1 is the natural logarithm of the ratio<br />
between the virtual populations of the age of x-+ 1 years and of x years
•<br />
'Table 55. Values of the total mortality (by using the<br />
captures by net per unit effort).<br />
Season<br />
Number of salmon/100nets<br />
Total A.1+ A.2+ A.3+ A.1+ A.2+<br />
_<br />
1956/57<br />
1957/58<br />
1958/59<br />
1959/60<br />
1960/61<br />
1961/62<br />
1962/63<br />
7,5<br />
9,2<br />
13,3<br />
10,5<br />
. 8 , 5<br />
10,0<br />
8,0<br />
5,8<br />
.5 , 0.1<br />
9,6<br />
5,2<br />
6,6<br />
9,0<br />
5,9<br />
1,6<br />
3,6<br />
3,2<br />
4,9<br />
1,8<br />
0,9<br />
1,9<br />
0,1<br />
0,5<br />
0,4<br />
0,3<br />
0,1<br />
0,1<br />
0,1<br />
0,48<br />
0,45<br />
0,67<br />
1,06<br />
1,99<br />
1,55<br />
1,16<br />
2,20<br />
2,36<br />
3,89<br />
2,89<br />
2,20<br />
• Min e . = Mean 1,03 2,45 .<br />
- 20 2 -<br />
(N. N. 19 6 2). The values obtained with this method amount te an aver-<br />
age in the Second year Z 2 = 1.15 and in the third year to z 3 = 2.74..<br />
Table 56. Determination of Z with the aid of the virtual<br />
population.<br />
• Number of salmon caught Coefficient of f -Ff•<br />
Season<br />
-<br />
the total loss<br />
n n+1<br />
-<br />
Total A.1+ A.2+ A.3+ Z 2 z3 2<br />
\ \ \<br />
1956/57 93 200 71 800 19 500 1 800 1,31 1,94 4,68<br />
1957/68 49 700 26 900 19 400 2 800 0,58 2,37 3,96<br />
1958/59 62 600 45 000 15 000 1 800 0,96 2,71 3,94<br />
1959/60 36 900 18 100 17 300 1 000 0,42 3,36 4,56<br />
1960/61 55 400 42 800 11 900 600 1,71 3,67 5,16<br />
1961/62 86 000 77 800 7 700 300 1,94 2,40 5,43<br />
1962/63 47500' 35 300 11 100 700<br />
mind. = Mean 1,153 2,742<br />
•<br />
1 On account of the ice conditions only 32,400 salmon were<br />
caught in six Months. For the determination of Z the cor-<br />
responding figure for 8.8 months = 47,500 salmon had to be<br />
used as basis.<br />
Kandler (1964) has also used the total German landings as basis<br />
for the determination of Z. The division of the yields into the age classes,<br />
howevei", waS carried out with the aid of the divisons by weight (cf. 5.33.).<br />
The mean Value obtained by him for 1958/64, Z = 1.14, agrees quite well<br />
with the values found here.
• 7.2.2.<br />
•<br />
ideeting through fishing and natural mortality<br />
-203-<br />
By way of introduction (7.2.) it had been emphasized that the<br />
losses<br />
total losses are composed of the waet-i4ig through fishing, the natural mor-<br />
tality and the spawning migration. If we designate these losses by F, M,<br />
[p. 350 ]<br />
and T (transport) and when we see them like the total mortality Z asex-<br />
ponential coefficients, we then have<br />
Z = F + (M + T).<br />
The losses through the spawning migration are not found in this<br />
form in other stocks of fish. The migrating salmon are a practical loss .<br />
from the stock in the sea. Thus the total losses are increaSed. To begin<br />
• with, (M + 72) isicAcé considered a unit in comparison with F.<br />
7.2.2.1. The results . of tagging<br />
Tagging of artificially reared and naturally grown smolt has<br />
- been carried out oh a large scale. The recaptures do not, however, give<br />
satisfactory resuits in regard to the mortality during the exploited phase.<br />
The experiments have shown hitherto that the emigrating smolt become con,-<br />
siderably redUced in numbers during their first year in the sea (recruit-<br />
ment phase). It has hitherto not been possible to ascertain exactly the<br />
total losses during this period. Therefore, the number of the surviving<br />
salmon thatreach the exploited phase is not known.<br />
Carlin (1959a and 19 62a),was able to provide the first picture<br />
of the conditions of the stock with the aid of the method of exclusion<br />
and a few assumptions. Of the -tagged salmon that survived the recruitment<br />
phase about 34 per cent were caught during the second .year in the Baltic<br />
Sea; in the following year 48 per cent of the survivors fell prey to fishing..<br />
.(average of the years 194 to 1958). The corresponding figures for later<br />
( 4 )
- 204<br />
experiment were about 40 per cent and 60 per cent, respectively (1958 to<br />
1960). . •<br />
It is.possible to recognize the effect of fishing rather more<br />
unambigUously, when adult salmon have been tagged in the sea. Blair (1955)<br />
tagged in June 1940 6.8 salmon and 386 grilse in the sea near Newfoundland.<br />
After one year 41.2 per cent of the salmon were recaptured and 1.5 per cent<br />
in the second year. For grilse the corresponding figures were 36.6 per cent<br />
(1st year), 2.6 per cent (2nd year) and 0.3 per cent (3rd year). Belding<br />
arid Préfontaine (1961) tagged in June 1938 195 salmon at the northeast<br />
6(0<br />
coast'of Newfoundland, of which 21.8 A were reported back. Along the Irish<br />
coasts 4562 salmon and grilse have been tagged between 1948 and 1961. The<br />
average rate. of recapture was 26.4 per cent (A. E. J. Went 1964). In Nov-<br />
ember 1960 and in December 1962 we have tagged on board of salmon cutters<br />
86 salmon of the sea year class A.1+ and 13 fish of the sea year class A.+.<br />
During tlie first year 18.6 per cent of the older fish were . reported from<br />
the Baltic Sea and 9.3 per cent from rivers or their estuaries of the Gulf<br />
of Bothnia. The recaptures of the gmall fish amounted to 15.4 per cent in<br />
the Ilaltic Sea during the first year. A division of the larger salmon int o .<br />
those that were liberated in good condition and others that were in medium<br />
condition when liberated, gives for the first group 20 per cent recaptures<br />
from the Baltic Séa and 13.3 per cent from the rivers. This material by<br />
*itself is too small for the derivation of the mortality coefficients. It<br />
may, however, be of some value for comparison with other results.-Wé obtain<br />
(Pss<br />
the wes4e through fishing with the aid. of a proportion (Beaverton and Holt<br />
1957). The total number of thé dead stands in the same proportion to the<br />
number of captured fish as the total mortality.to that caused by fishing.<br />
No-Nt Z<br />
F<br />
11 . number at the time t 0 -<br />
Nt = number at the time t..
According to (2) we obtain,from this<br />
-F<br />
• nZ<br />
N0(1 - e -Z ) .<br />
- 205 -<br />
By using the average value of the total mortality of 1.41<br />
(Table 54) one obtains for the salmon in good condition<br />
F = 0.37 for the Baltic Sea,<br />
F = 0.62 for the Baltic Sea and the rivers.<br />
7.2.2.2. Determination with the aid of the intensity of fishing<br />
Wellave already 'seen (4) that the coefficients of the different<br />
rates of loss (M + T) and F add up to the total mortality Z. There is no<br />
'doubt that M is very small for the adult salmon in the Baltic Sea, where<br />
they have practically no enemies 1 5. iiitherto there have been no reliable<br />
investigations of the share of the 'salmon in the sea year class A.1+ that<br />
migrate to spawn (T). The average values that are shown in Table 39 are •<br />
insecure and it was not possible to cOnsider annual changes. In the eXam-.<br />
ination of thé sea year elass A.1+ We dhall therefore considet (H + T) as<br />
constant. Under these premises, all changes in Z must be attributed quan<br />
titatively to corresponding changes in F. Since the loss through fishing<br />
is proportional to the intensity of fishing f, respectively to the ex-<br />
penditure, we fine from (4)<br />
Z = cf + (M + T).- •(5)<br />
When Z and f are known, c and (M + T) can be obtained by the<br />
methoe of least squares.<br />
In thè.calculation of Z we had assumed that the values of the<br />
15 .<br />
landroth (1962) was able to demonstrate that the harbour porpoise, long<br />
considered *to be a salmon predator, does not eat salmon.<br />
:ID • 351 I
- 206-<br />
strength of the stock N pertain to a certain time t. If, however, the<br />
density of population is specified as the mean value for a fishing period<br />
U,thenthe Z-values are not quite correct. The average annual number of<br />
fish amounts to (Beverton and Holt 1957):<br />
= _E_ ( 1 _ e t).<br />
• Here N is the number of fish at the beginning of the period t.<br />
For the years 0 and 1 one obtains; •<br />
° ' '112 ( 1 - e - Z0)<br />
Zo<br />
= -1 (1 - e1)<br />
Z1<br />
The division of the two equations, whereby, according t<br />
•<br />
one sets N 1 = No e. Zo, results in<br />
. --<br />
e—Z)<br />
zn — In + ln<br />
Z1 (1--e-zo) and . on account of (5),<br />
No•, (cfo + M + T)(1,—e--(cf, +M . 11')).<br />
,= In<br />
In (cf t + M + T) (1 — e-(cr.0 m +T))<br />
( 1 ) ,<br />
In order to çalculate Z the second 'term at first approximation<br />
is set equal to 0 and we obtain<br />
cf o + (M+T) = Zo. = In<br />
iNt<br />
. .<br />
One can now calculate c and (M + T) with the values for Z and<br />
1 • Inserting these into (6), one obtains new results for Z, which are<br />
b. 352]<br />
used once more td -obtain improved results for c and (M + T). The three-<br />
to four-fold repetition of this procedure leaàsto constant results (iter •<br />
àtive method).<br />
Beverion and Holt (1957) used the iterative method to calculate<br />
F. If one uses this•equation for the values Of Z and f in Table 54, one<br />
obtains a négativaresult for (M + T). The failure'of the method can have<br />
two causes. Eiiher the changes in Z are not caused or not caused solely '<br />
(6)<br />
. •
•<br />
- 207 -<br />
by changes in the intensity of fishing f, or the scatter of the values of<br />
Z and f (that is, their error) is so large that the method remains without<br />
success.<br />
On the' other hand, Christensen (1964) was'able to obtain with<br />
the aid of the iterative method results of F 2 = 0.73 and (M + T 2 ) = 0.60<br />
(cf. 7.2.1.). If we now compare the data on which the two cases are based,<br />
in order to find an indication of possible sources for errors, we find that<br />
the correlation of the values for the -e-ap-te per unit effort (line) gives<br />
a correlation-coefficient of rc = +0.93. There is also a high correlation<br />
with ra = +0.94 between the two determinations for the age composition<br />
c.lutbi-<br />
e-84 per unit effort of A.1+). On the other hand the correlation Coef-<br />
ficient for the values of the fishery expenditure is considerably lower<br />
with rf = + 0.82. This indicates that the German figures for the fishery<br />
expenditure do not represent the total expenditure with sufficient exactness.<br />
'Faloheimo (1961) has developed a linear equation that makes un-<br />
necessary the iterative method in the determination of F and (M + T). For<br />
this purpose the second term in equation (6) has been set . K. When<br />
- ln 7 aZ, then<br />
aZ 1<br />
+ aZ o'<br />
The equation is decisively transfoimed through the determination<br />
of a. For the calculation of the infinite series of<br />
•<br />
- 1.11<br />
-Z<br />
1-e<br />
only the first term was used, whith the . result that a = 1/2. For Z.c1 the<br />
error in - a = 1/2 is less than 10 per cent. Since the value of the second<br />
term in equatiOn (6) is small compared with the first term, this approx-<br />
imation may be permissible. Equation (6) then becomes;
•<br />
N„<br />
Z o = cf„ (M1- T) -- In — 1<br />
No.<br />
cf„ -(M+T) =- In NI +<br />
N o<br />
In NI cf„ (M+T) —<br />
----i--- (Z — Z1)<br />
`)<br />
1<br />
(f0 f1)<br />
1<br />
(fo f1)<br />
N 1<br />
In ° — 2 c U 0 17 f + (g+T)<br />
— 208—<br />
Paloheimo has established that his linear equation is superior<br />
to the iterative method in all bases when deviations are introduced through<br />
ceta-<br />
defective material (age, c-ape per unit effort, figures for landings)<br />
or through changes in c. The cause for this is to be seen in the fact that<br />
Z 1 is not being correlated with f 1 but with 1/2 (f 1 + f 2 ). An improvement<br />
can only be expected when c is strictly constant and when only the cep—<br />
P. 353]<br />
tuegs per unit effort per age group are erroneous. In all .other hypothet-<br />
ical cases the standard deviation of c and M was reduced by from 27 per<br />
cent to 69 per cent in comparison with the iterative method. The application<br />
of the linear equation of Paloheimo to the values of Table 54 results in<br />
the equation<br />
Z2 = 0.2135 f + 0.288.<br />
Since Z 2 7 1.23 on an average for the years 1956/57 to 1961/62<br />
. we obtain (line catches):<br />
Z,<br />
(M + T) 2<br />
1.23<br />
0.29<br />
F<br />
2<br />
0.94<br />
The total mortality that has been obtained with the aid of the<br />
netting values Can also be dorrelated with f according to the method of<br />
Peoheimo.<br />
Z 2 1.03<br />
(M + T) 2 0.28<br />
F 2<br />
0.75<br />
(7)
•<br />
- 209 -<br />
If one uses the method of the virtual population and then cor-<br />
relates the values,of Z.thus obtained again with f after Paloheimo, then<br />
the losses during the second year in the sea amount to<br />
Z 2<br />
1.153<br />
(m + T) 2 0.261<br />
F 2 0.892<br />
Through the above explanations it has become clear that the<br />
available data do not form a reliable basis for the determination of the<br />
'loss coefficients. Since the total - mortalities that have been calculated<br />
after Beverton and Holt and with the aid of the virtual population in A.1+<br />
provided nevertheless rather.goo1 agreement we shall have to reckon with<br />
,<br />
errors in the values of the fis rykxpend ture, as had already been sus-<br />
pected during the comparison with thé results of Christensen (1964). The .<br />
values of F 2 do not agree approximately with the results of tagging. These<br />
will therefore be left out of consideration. The rounded-off loss data are<br />
now<br />
Z, 2 1.2<br />
Ovi + T)<br />
2 0.9<br />
0.3<br />
F<br />
2<br />
None of the methods mentioned so far gives usable values for<br />
the losses in the thi.rd year in the sea. In all cases negative figures were<br />
obtained for M. In order to obtain an idea of the order of magnitude of<br />
the losses, we can use the mean value of Table 54 for z 3 . If we assume<br />
F 2 = F3.. we find<br />
Z . 2.2 .<br />
• 3<br />
0.9<br />
(M .4- T) 3 1 .3.<br />
. Withthese Values We have.now two equations with .the three<br />
•inknowns M, T 2 and T 3 . For the calculation of the natural mortality and
— 210—<br />
the coefficient for the spawning migration, however, three equations-are<br />
required.<br />
When No . = number of salmon at the beginning of exploitation during<br />
the second year in the sea<br />
N t1<br />
« Nt2 =<br />
= survivors'after the second year in the sea<br />
then we have according to (1)<br />
survivors after the third year in the sea<br />
Ntl =<br />
No e- Z 2t 1<br />
No - Ntl = No (1 - e -Z2t1 )<br />
«Nt2 = Nt1 e-Z3(t2 t1)<br />
Nti - Nt 2 = N e -Z 2t 1 (1 _ e - Z3 1 t2 t11)<br />
When one multiplies the total losses (8) and (9) with the ex-<br />
(8)<br />
[P. 354]<br />
(9)<br />
pression T.2/Z 2 and T3/Z 3 , respectively, one obtains the number of spawning.<br />
migrants (Béverton and Holt 1957) after the second and third year, respec<br />
- tively. The division of the equation results in<br />
Ta • Za e • z29(1 — e—zet2<br />
_ T2.. Z3(1 -<br />
C11)<br />
. _<br />
(10)<br />
This ratio oan be taken from Table 37 as 41/80. With this we<br />
have three equations.. Through insertion of the first two equations in (10)<br />
one can calculate the natural mortality. However, with the data at hand,<br />
E becomes negative, Since we know already from.other determinations that<br />
M is very small in the exploited phase, whereas for (M T) in A.1+ a<br />
« coefficient of-only 0.3 has been round, we shall assume for the time being<br />
M as 0.1.<br />
- Christensen (1964)-, who used the sanie method for the deter-<br />
minatdon of M and T, could take the numerical ratio of the spawning migrants<br />
from the Swedish tagging experiments. He arrived at values of M = 0.103, -<br />
T 2.<br />
T 5. = 1..397. .
7.3. Losses in the recruitment phase<br />
- 211 -<br />
We designate here as the recruitment phase the period of life<br />
from the emigration from the rivers to the beginning of exploitation.<br />
This period comprises on an average slightly less than 1.5 years, since<br />
the salmon enter the exploited phase only in the fall of the second year<br />
in the Sea.<br />
7.3.1. The natural enemies<br />
We have a number of papers that treat the enemies of the salmon<br />
fry and of the parr. • here are only a few investigations of the losses in<br />
smolt- White -(1936) found in the river Màrgaree (Nova Scotia) that king-<br />
fisher (Megaceryle) and mergansers (Mergus) had eaten daily more than 40<br />
fish (salmon, sea trbut, sticklebacks). The mergansers alone consumed<br />
390,000 smolts of salmon and sea trout. Huntsmann (1941) could show with<br />
the aid of tagging that the number of. emigrating smolt could : be more than<br />
doubled when kingfishers and mergansers were controlled. Elpson (1962) even<br />
obtained a five-fold increase in the nùmber of migrating smolt.through the<br />
control of kingfisbers and mergansers.<br />
In the Betio Sea similar investigations have been carried out<br />
hitherto by Lindroth (1955a). In the Indalsâlv the mergansers had eaten<br />
preponderantly the Parr of salmon and sea trout. One hundred adult and one<br />
hundred and tWenty-five juvenile mergansers -consumed from June until Sep-<br />
tember 350,000 parr. The annual production of smolt in the Indalsâlv is<br />
around 3504000. These investigations show that the losses of smolt alone<br />
through Mergansers and kingfisheré can amount to 50 to 80 per cent. , •
- 212-<br />
In a further paper Piggins (1958) treats Irish salmon smolt.<br />
With the aid of tagging he ascertained the losses in the region of the<br />
Burrishoàle fishery. A total of 5224 ' -fteh were tagged, of which almost<br />
3100 were smolt, the remainder being parr. One hundred and fifty-six 6f,'<br />
the tags recovered were found in the stomachs of predators.<br />
' According to Piggins, herons are commonly found in the region<br />
in question; These birds have no enlarged pyloric antrum and usually void<br />
the tags within 12 hours. Five birds.examined had four tags in their<br />
stomachs. In order to avoid making to4iigh an estimate of the losses, we<br />
shall assumethat one heron had eaten on an average only two tagged salmon<br />
during the months in question, namely . October to December, which would<br />
amount to 200 fish for 100 bird.<br />
. Of the frequently encountered mergansers 15 birds were.examined,<br />
which contained eight tags. Since these are retained in the stomach for<br />
lengthy periods, one can reckon that 150 mergansers had eaten only 80<br />
tagged fish.<br />
'Cormorants.are very common, but also have no enlarged pyloric<br />
antrum. Although previously up te five smolt had been found per bird, no<br />
tags could be found in 22 birds. We estimate the losses through cormorants •<br />
therefore as only 20 tagged fish.<br />
The pollack (Pollachius pollachius) enters in spring in large.<br />
the estuaries of the Burrishoole region. In 94 pollacks only un-<br />
numbers<br />
marked fish were found On the 1st and 5th of May, whereas the tagged smolt<br />
were first liberated on May 1, and 5. Of further fish examined six pollacks<br />
contained 12 tags at the end of May. According to Piggins all Pollacks eat<br />
gmolt and follow them intô the sea in June. Formerly more than 60 per-haul
- 213-<br />
were caught with seines in Mar. Since they are not being fished at present,-<br />
one must reckon with 1000 fish in the'region in question, these Must have<br />
eaten at least 500 tagged fish.<br />
Brook trout of a length of 23 to 33 cm are represented as the •<br />
most important predators of salmon. These robbers retain the tags in their<br />
stomachs for at least four months. Of the fish examined (total number un-<br />
known), ,20 fish . contained 134 tags. Since the brook trout forms . a strong<br />
stationary stock, one can reckon with 1000 fish, who consumed a total of<br />
2000 tagged salmon.<br />
With these minimum assumptions one obtains the number of 2800<br />
tagged salmon that had been eaten by the predators cited. That corresponds<br />
to a loss of 54 per cent in the estuary alone and principally within,four<br />
months. As has been mentioned above, it is true that a series of parr have<br />
been included in the investigations 16 .<br />
7.3.2. The mortality until the beginning of exploitation<br />
The above statements of the present paper show that the numbers<br />
of salmon in the recruitment phase are being reduced quite heavily. With-<br />
out doubt, the decisive losses take place during the period bêtween eMie<br />
ration and the transition to pelagic fish food. The smolt at that time<br />
constitute a' disturbing element in the equilibrium of the population mech-<br />
anism of the-other dwellers in the sea. They are being forced to learn<br />
an entirely new behaviour for their conduct in life. Instead of the pos.-.<br />
sibilities of hiding that they had in the rivers, now only speed is of<br />
avail against predators. The relations.between predator and prey have<br />
16 According to Piggins, the smolt losses have to be set at 70 per oent<br />
(personal communication).
- 214-<br />
shifted and the fOod supply has changed. There are other competitors.<br />
Finally, the young fish are confronted by an entirely different physical<br />
environment.<br />
If one wants to view this complex multiplicity of phenomena as<br />
a constant cause of the natural mortality, this would obviously mean a<br />
coarse simplification. However, we are today not yet in a position to make<br />
statements about the fluctuations in the stocks of the predators and in<br />
the food supply. We can therefore only attempt to estimate the average<br />
total losses for a longer period.<br />
Kgndler (1958) has used the share of tagged salmon in the total<br />
captures and the number of tagged smolt released in order to ascertain<br />
the number of the emigrating young salmon in 1955 and 195 6 and arrived at .<br />
[pw 356 ]<br />
a figure of five to six million fish. Lindroth (1956) states the natural<br />
production of smolt in the Swedish rivers to have amounted to about four<br />
million Salmon before the building of the power stations. Since the Swedish<br />
share in the production in the Baltic Sea is estimated generally to be ca.<br />
65 per cent, one obtains a total number of smolt of about six and one-half<br />
million of smolt.<br />
If we càrry out the investigations in the manner of Kgndler for .<br />
the average of the years 1956/57 to 1962/63, we find that the weighted<br />
share of tagged salmon in the German captures was 0.902 per cent. Against<br />
this we have the number of 71,600 tagged smolt that were liberated in the<br />
average of the years 1955 to 1961 (B. Carlin 1962a). From these figures<br />
we deduce that almost eight million emolt . emigrated on an average during<br />
1955 to 1961. Ildw Carlin (1962a) has shown that the percentage of recoveries<br />
has increased froffi.year to year. Among other things, this points to a mor-<br />
ftality related tb tagging or to incomplete recoveryreports..If we assume
- 215 -<br />
the share of the tagged fish as one per cent, we arrive at a production<br />
of Seven million smolt.<br />
According to the reports available, one may assume that the<br />
losses are very high during the first three months after entering the<br />
Baltic Sea and that they then diminish quickly until the exploited phase.<br />
Let us once more summarize the data cited. The number of the gmolt migrating<br />
into the Baltic Sea.is about six to -seven million fish. In some Canadian '<br />
rivers running into the Atlantic Ocean and in Ireland the losses during<br />
the smolt migration amount to 50 to 80 per cent.<br />
On the basis of tagging of smolt and by assuming the natural<br />
mortality during the exploited phase as 20 per cent Carlin (1962a) arrives<br />
at a loss figure for the first year in the sea of 83.4 per cent.<br />
7.4. Models of the stock of. salmon in the Baltic Sea<br />
In order to test with what approximation the parameters ascer-<br />
.tained correspond to the actual conditions, it will be most instructive<br />
to present the life cycle of an average UZ-e44<br />
We obtain the number of recruits at the beginning of exploi-<br />
tation by using as basis a migration of six and one-half million smolt<br />
and the figure for the loss of Carlin of 83.4 per cent. For the further<br />
calculations the équations (8) and (9) apply.<br />
The parameters.thus ascertained have been used in Table 57.<br />
Since no coefficients of loss could be calculated for the fourth year,<br />
we have here assumed a loss . through fishing of about 55 per cent. The<br />
number of survivors at the .beginning of the fourth year is very émall,<br />
so that it does not Play a Substantial rdle for the total stock.<br />
TwO items of knowledge can be gleaned from Table 57. The first.
- 216 -<br />
concerns the yield of captures. If we set the total number of the captured<br />
fish equal to 100, we obtain for the three sea year classes shares of 75<br />
22, and 3 Per cent. On the other hand the average values of the age analyses<br />
(Table 33) are 69, 28, and 2 per cent. The parameters ascertained are there-<br />
fore erroneous, so that the model does not agree with the actual conditions.<br />
An alteration of F or of Z changes the percentage of the fish caught in<br />
the second year only unsubstantially. The decisive and important knowledge<br />
to be derived from this fact is the - determinationthat the fishing is sel-<br />
ective, - so that the sea year classes are being exploited - in different de-<br />
grees. The expectatiOn that F is equal in both sea.year ailases is wrong,<br />
P 3 must be greater than F 2 .<br />
The . second . item concerns the number of spawning fish. In Table<br />
57 the number of spawning migrants of the sea year class A.2 issmaller<br />
than the number of three-year-old spawning fish. However, we know already<br />
that the relation is the opposite (5.3.1.3.). With this we have two orit-<br />
! [p. 357]<br />
eria, with the eViofleioh the parameters can be tested. For the final res-<br />
ults it will be of value, to pursue this idea further.<br />
Table 57. Preliminary model of the stock of salmon in<br />
the Baltic Sea.<br />
Coefficients<br />
of<br />
.<br />
Num.<br />
Years at Number Yield of<br />
in .beg,- of fishery<br />
the in. natur..<br />
loss Balt, of losses Number<br />
F T Sea year<br />
. Number<br />
of<br />
spawn. Total<br />
mi-<br />
grants -<br />
1. 6 500 000 5 421 000<br />
5 421 000<br />
0,1<br />
0,1<br />
0,9<br />
0,9<br />
0,2<br />
1,2<br />
2.<br />
.3.<br />
4.<br />
1 079 000<br />
324 995<br />
36 009<br />
62 808<br />
13 134<br />
565 504<br />
118 224<br />
(20 000)<br />
1 700<br />
890<br />
200<br />
125 693<br />
157 628<br />
754 005<br />
288 986<br />
703 728 2 790
• To<br />
1<br />
T.,<br />
T3 • Z2 • e — z2ti (1 — e—z3(12 —(1))<br />
Z3 • T2 (1 - e—z2ti)<br />
— 0,51<br />
— 0,51<br />
- 217 -<br />
begin with, we have to establish which parameters exert the<br />
decisive influence in the numerical ratio of the salmon that migrate to<br />
spawn in the second and third year in the sea. According to (10) we have:<br />
c—zeiZ.) 1 — e-23(t2—ti)<br />
•T3 •<br />
c-Z2t1 Z3<br />
The result of the proportion is determined by T 2 , Z 2 , T 3 and<br />
(ii)<br />
Z 3 . It can be said at once the influence is small of T 3 and(T3), measured<br />
- on T2 and Z 2 . If one accepts as perniissible a deviation Of the result of<br />
0.051 (10.per cent) and tries with the possibilities of combination of.<br />
.the figures of Z 2 .= 0.9 to 1..5; T 3 . 0.8 to 1.4, and z 3 = 18 to 2.5, one<br />
will find that T 2 can take on values of only between 0.3 and 0.6, because<br />
the deviation of 0.51 amounts in all other cases to more than-20 per cent.<br />
Since we can assume that F 2 is not smaller than T 2 , the number of possible<br />
combinations.can be restricted still further.<br />
• Let us now look first at the numerical proportion of the salmon<br />
caught in the second and in the third year in the sea. The value of this<br />
proportion can be taken from Table 33 as 69.364:27.575 = 2.516. One obtains<br />
the nuMber of the salmon captured during the second year in the sea by<br />
multiplying (8) with F2/Z 2 . The corresponding expression for the third<br />
year is obtained by using (9). The division of both equations results in<br />
' N„ (I — e-2z2 , 1)<br />
Z2<br />
F3<br />
• • N„ e e—T2.11 (1 — e—z3(t2—tt.)<br />
. 1 Z3 1<br />
. - .<br />
.(!---(F2 - : W. 1 1 • z.) F 3 1—e—z3(t2---1,) •<br />
- 2,516<br />
No value can be expected for M that . deviates . substantially from 0 .1,<br />
( 1 2)<br />
because . the salmon has no enemies in the exploited phase. The influence
nachafter<br />
00 04<br />
0,3<br />
0,4 2 1<br />
0,5 6 9<br />
0,6 11 15<br />
• 0,7 11 14<br />
0,8 5 3<br />
0,9<br />
T2<br />
_<br />
afte<br />
(31) (12)<br />
0,2<br />
0,3 2 7<br />
0,4 16 16<br />
0,5 13 13<br />
0,6 4 ' 6<br />
0,7<br />
- 218-<br />
of F and z 3 on the result of the proportion can only be small. There-<br />
3<br />
fore the numerical ratio between the salmon caught during the second and<br />
third years in the sea is determined principally by F 2 and T 2 . If we now<br />
try to obtain an approximation to the actual values of the parameters<br />
with the aid of equation (12), then the poèsibilities of combination can<br />
[p. 358 ]<br />
be reduced considerably through the limits for T 2 that have been obtained<br />
with the aid of (11). A.deviation of .± 0.126 (5 Per cent) for the value<br />
of the proportion will be considered as permissible. The remaining pos-<br />
sibilities result in the following distribution of frequencies for F 2 and<br />
T 2 :<br />
one obtains:<br />
ana T,:<br />
The weighted mean of these series amounts to for<br />
F 2 = 0.63<br />
T 2 = 0.45<br />
. With M = 0.1 it is then<br />
Z 2 = 1.18.<br />
When these values are inserted in the equations (11) and (12),<br />
Z3 2,0901 F3 (1 — e—zs (t2—ti))<br />
Z3 2,2$05 T3 (1 e—zs (t2*tI))<br />
The division of the two expression results in:<br />
Since<br />
1,0911 T3<br />
Z3 F3 + T3 «<br />
Z3 = 2,1911 . T3 '<br />
We thus have three equations from which we can calculate F3
E3 = 1,61<br />
T3 =-- 1,48<br />
M = 0,1<br />
4 3,19<br />
and with<br />
we have<br />
The values that have been used as basis in Table 57 result in<br />
a yield of the fishery of more than 700,000 salmon. This figure is with-<br />
out doubt too high (cf. Table 16). For the erection of the final model<br />
of thestock we shall start with a number of recruits that results in thè<br />
capture of about 450,000 salmon. . This figure represents approximately the<br />
conditions of the last years. If again the losses in the first year are<br />
• f<br />
assuMed as 83.4 per cent (Carlin 1962a), the number of smolt is 5.1 mil-<br />
lion. This figure is about one 'million lower than the values cited earlier .<br />
(Lindroth 1956, ehdier 1958). This difference can have three possible<br />
causes. (1) The paXameters of the revised model are still too inaccurate.<br />
(2) The number of smolt arrived at hitherto has been too hdgh an estimate.<br />
(3) When the mortality during the first year is higher for the natural<br />
smolt than for the artificially reared ones, then the losses may amOunt<br />
not to 83.4 per cent, but to abolit 86 per cent.<br />
The percentage losses can now be obtained on hand of the revised<br />
results given in Table. 58. On an average the fishery removed about 37 per<br />
cent from the sea year class A.1+ and about 48 per cent from the sea year<br />
class A.2+ of the fish present at the beginning of the year (Canin 1962<br />
figured with 40 and 60 per cent, respectively) . . The corresponding natural<br />
[P.359 ]<br />
mortality was 6 or 3 per cent, respectively. Of the salmon present at the<br />
. beginning of the season, 26 . per cent of the sea year class A.1+ and 44<br />
per cent of the sea year class A.2+ emigrated in order to spawn. The<br />
total losseS in class A.1+ :amounted to 69 per cent; those in class A.2+<br />
were 96 per cent. After two years there were still present 13 per cent<br />
- 219<br />
-
•<br />
1. (5 100 000) (4 250 000) 4 250 000<br />
0,1 0,63 0,45 2. 850 000 49 900 314 352 943 224 543 588 795<br />
0,1 1,61 1,48 3. 261 205 7 852 126 412 948 116 205 250 469<br />
4. 10 736 (6 500) 65<br />
2.-4. Jahr 1 . 121 941 447 264 1 956<br />
- 220-<br />
of the recruits that just entered the exploited phase. The exploited<br />
total stock comprised about 1.1 million fish, of which about 76 per cent<br />
belong into the sea year class A.1+. There exists a difference between<br />
the age composition of the stock and that of the captures (69 per cent<br />
A.1+) because the fishery is selective.<br />
Table 58. Revised model of the stock of salmon in the<br />
Baltic Sea.<br />
• Num .<br />
.<br />
Coeffi- Years at Nàmber<br />
' cients in beg- of<br />
of the in. natur.<br />
loss . Balt. of losses<br />
Yield of<br />
fishery<br />
Number<br />
of<br />
spawn.'<br />
mi-<br />
Total<br />
. M •F TSea year Number t grants<br />
The two most important results of the statements will be<br />
summarized once . -more:<br />
It is of •great iiaportande that the sea year class A.3 is being .<br />
fished . selectively. As a possible cause should be mentioned the selec-<br />
tive effect . of the driftnet fishery. The amount' of the exploitation of<br />
the salmon of the sea year class A.1+ is of extraordinary influence.<br />
Small changes in F 2 have a. substantial effect On the entire stock.<br />
In contrast to .this,changes . in F 3 do not play a great role. It will<br />
have to be the object of further investigations to test the parametera •<br />
presented so . as . to obtain an•unembiguous indication of the extent of the<br />
conservation effects that ean be obtained throngh elhangee in F 2 .
Summary<br />
The fishery on salmon in the Baltic (2)<br />
– 221 –<br />
. There were 3 periods of development in ,salmon fishing. Up to the commencement of the 18th<br />
century only river fishery has been carried .out. From this fishing in the coastal regions was<br />
being evolved. On account of the introduction of drift-lines and the resulting good catches in<br />
the open Baltic, deep-sea-fishing has been;;developed after the year 1945. For the time being it '<br />
is still of greater significance:than river and coastal fishery.<br />
The total fishing effort in deep -sea-fishery his increased since 1955, although the number of<br />
vessels has decreased (Tab. 5). For the time being' about 350 'vessels froin Danmark, Sweden,<br />
Poland and West Germany are carrying out salmon fishing. Of these some 150 are operating<br />
with drift-lines only and 200 with drift-nets additionally .(2.3.3.1.).<br />
The catch Per unit effort is ex:pressed in number of salmon per 1000 hooks or per 100 nets<br />
andiday. It is not an exact expression of abundance, because the data are'biased. by uneven<br />
ditribution of salmon within the stock area by influence of the wind, by food supply, .food<br />
competition and gear selection. Generally. the temperature conditions and the distribution of .<br />
individuals may not influence the cOmparability of the values from year to year (2.3.5.2.).<br />
Food coMpetition of cod (gear saturation, 2.3.5.) may result in an error of not more than 0,5<br />
salmon per 1000 hooks. Variations in the natural food supply do affect the drift line catches in<br />
so far as there is a competition bêtwe.en the amount of natural food and bait (effort) (Tab. 9).<br />
There was no pcissibility to ellininate thé effects of these factors (2.3.3.2. and 2.3.5.), Wind of<br />
more than 5 Beaufort results in better catdies than wind of less than 5 Beaufort (Tab. 10). Drift<br />
net catches are dianging vice versa (Tab. 11), the differences being statistically significant. The<br />
catches are also being correlated with the direction of the wind (Tab. 10, 11).<br />
• Tests with hooks of different size did not result in statistically significant differences of the<br />
•catch. The seleçtion .first of all is in correlation with the size of the bait.. An average sprat has .<br />
a body height of 25 mm and maY be swallowed by a salmon of 27 cm in length.<br />
Drift nets are acting highly selective. Only very few big individuals may escape but a lot<br />
of small salmon are not caught. In case of a mesh%ize Of 78.75 mm between knot and knot for ;<br />
nylon nets the 50%-retention-length amounts' to 78 resp. 105 cm of the total length (fig. 10).<br />
Corrected figures of catch per unit effort are suinmarized in 'I'ab. 15.<br />
The total yield of the salmon and sea trout fishery in the, open Baltic and Baltic rivers are ;<br />
shown in Tab.. 16 and appendix III–V. . •<br />
The sex conditions (3)<br />
'File proportion of sexes is correlated to the changes in thé abundance of the year-classes (3.1.):<br />
Recruitment oocytes with a diameter of less than 0.3 mm and maturing, oocytes, rich in .<br />
yolk are present in eadi ovary (Fig. 15, 16). A discussion of the results of ovary investigations<br />
and estimations of the fat content as well as age determinations of the spawning and the fee- I<br />
shows the following results: Salmon of a fat content of about 12°/s in spring and a . cling stock<br />
mean diameter of the oocytes of more than 1.5 mm will be spawning in autumn of the same<br />
year.<br />
_<br />
The Migrations (4)<br />
After downstream migration most smolts of the Bottnian Bay rivers stay more than 1 year in<br />
the Bottnian-Bay. Later on part of these turn to the Baltic proper together with the 1 year .<br />
; younger individuals from the Bottnian Sea (Tab. 22). No far reaching movements are carried<br />
out there. 'Ile migration is correlated with the search of food and wind (current) eff vets and<br />
the resulting distances do amount to not more than 10 km per day as an average. Normally ,<br />
there are groups of- 2-10 individuals. By influence of wind and food effects crowds :a more ;<br />
salmon are being formed. But . even then there is no shoaling, beause in the densest concentrations<br />
the indiyiduals have an average distance of more than 10 m from cadi other. ,<br />
• .<br />
. Age and growth (5)<br />
The relation between total length i...t and fork length Li is being expressed by '<br />
• Lf = - 1.2256 -I- 0.9578 Lt.<br />
Lt 1.2796 + 1.0441 Lf<br />
the eqùations possibly being valid for the whole stage of sea life (5.1.1.). A linear•relation also<br />
exists betsven gutted weight Wie and fresh weight W.<br />
• . Wic ----- — 0.0241 --h . 0.918 Wf<br />
Wf ,----- 0.0263 + 1.089 Wg •<br />
Using the simple formula: . •<br />
•<br />
• • W g = 0.9114 Wf (Wg -=- Wf — 8.86 °/o) • • '<br />
. Wf =--- 1.0972 Wg (Wf ---- Wg + 9.72 %)
• •em.ilts<br />
- 222 -<br />
in an error Of less than ± 0.6 " 0 as far as salmon o. 10 kg in fresh weight are concer-<br />
ned and less than ± 1 Vo for salmon bet ween 1.6 and 20 L g fresh weight (5.1.2.).<br />
In Tab. 30 the number of sclerite rings formed during the first year of life or during the<br />
total river period resp. is correlated with.age. The corresponding correlation coefficients arc<br />
ri - 0.595 ± 0.0123 or r2 = 0.642 ± 0.0217 resp. (5.2.2.).<br />
As the mean smolt age amounts to 2.68 years (average 1958-1963), salmon of the southern<br />
Baltic are recruited to 1 /4 from rivers of the northern Bottnian Bay and to 3/4 from southern<br />
rivers. A smolt age of 2.4 years for the 1955 fry-year-class is thought to be related to an early<br />
smolt migration (Tab. 31).<br />
' As an average of the years 1957-4963 the proportion of the sea-age-class A.1 -I- amounted<br />
to 69.3%, the A.2 -I- class to 27.6% of the catches (Tab. 33). 50°/o of the spawning migrants<br />
took part in the reproduction after 2 years of sea life, ever 20-25% after one year less or one<br />
year-more (Tab. 37). The A.3 + sea-age-class consists to 37 0/o of individuals with spawning<br />
marks, the corresponding proportion of every elder age-groups amounts to 100 0/0 (Tab. 38y.<br />
The age composition of the stock is changing seasonally . A new smolt-year-class enters the<br />
exploited state between summer and autumn, whereas the maturing salmon start to leave in<br />
April. As a result the stodt composition shown in Tab. 33 is constant during the period November<br />
to Mardi (5.3.2.; 5.3.3.).<br />
The growth rate in length amounts to more than 30 cm during the first year in the sea, to<br />
about 28 cm during the second year, to about 20 cm during the third year, to about 8.5 cm<br />
during the fourth year and to some 5 cm during the fifth year. The corresponding growth rate<br />
-in weight totals to about 1 kg, 2 kg, 4 kg, 2 kg and 1 kg (Tab. 43, 44). The 1959 smolt-yearclass<br />
was shown to mark itself by an extraordinary growth resulting in a mean total length of<br />
80.5 cm in January of 1961 which is related to an excellent food supply during the first year<br />
of sea life (Fig. 36 and 5.4.2.2.).<br />
The size of smolts very possibly influences the growth rates during the sea life. This fact is<br />
not possible to be demonstrated directly, because individuals of higher smolt age are maturing<br />
first, so that the proportion of elder age-groups will decrease in the course of the years. That<br />
appears to result in salmon of higher smolt age apparently not to show a better growth rate<br />
than individuals of lower smolt agè (Tab..46).<br />
The food (6)<br />
Stomach investigations on 2400 salmon show the weight of food to consist of 75 0 /o of sprat<br />
and 13 Vo of herring. Besides garpike, sandeel and mysideae are of little significance (Tab. 48).<br />
The average weight of food amounted to 8.7 g between October and Mardi and to 39.3 g<br />
from April to June and in September (Tab. 49). There is a considerable difference in the food<br />
composition of young (A. -E) and old salmon (elder than A.1 -r) (Tab. 53).<br />
The daily food consumption may be within the range of 24 to 92 g, but very possibly much<br />
higher than 24 g per salmon. The weight of sprat taken by salmon may total to 10 000-20 000 t<br />
per year, that number being 50°/s of the total fishing yield (6.5.).<br />
Stock analyse (7)<br />
Calculation of mortality parameters by means of data on fishing intensity, catch per unit effort<br />
and age composition after the method of iteration resulted in negative figures for M. Better<br />
values have been arrived at from the PALOHEIMO equation (7.2.2.2.). Even these figures did not<br />
iced to a satisfactory model of the stock. But it has been shown, that fishing is selective, F<br />
being much higher in the A.2 + than in the Al + sea-age-class.<br />
Appointing certain ranges to the parameters and inserting these successively into equations<br />
(11) and (12) (proportion of the number caught [12] and the number of migrants [11] of the<br />
two sea-age-classes) resulted in better values:<br />
•<br />
A.1 : M = 0.1 F --- 0.63 T = 0.45<br />
•<br />
A.2 :M 0.1 F = 1.61 T 1.48<br />
In the 'beginning of the season the stock corisists of about 1.1 million individuals, after<br />
.being recruited by 850 000 salmon of catchable size. During the course of the season the fishery<br />
takes about 40 1/o of the stock. Some 31 °/o will leave the Baltic main basin in order to spawn<br />
but will be subject to coastal and river fishery.
R E . PERENCFS<br />
N. N., 1962: Course in methods of population analyses. Mar. Biol. Lab. Cronulla.<br />
— Bulletin Statistique, Vol. 1-45. ,<br />
AList, G., 1919: Mtirrumsans lax odi iaxiiring. Medd. Kg.l. Lbrstn. 216: 1-159.<br />
trout of lerrums&nl.<br />
nnd<br />
192â'a: The salmon - in the Baltic Area of Sweden. Rap. Proc. Verb. Vol. 48.<br />
— 1928b: Der Lulls und die Lachszucht in verschiedenen LI -indern. Ardt f. Hydr. •<br />
Lune salmon anc rearing oi salmon in various countriesj<br />
— 1934: Salmon in the Baltic precincts. Rap. Proc. Verb., Vol. 92. •<br />
— 1954a: The salmon catch and the salmon stodt in the Baltic during recent years. Vattenkr.<br />
foren. PubL, 1954. No. 5.<br />
— 1954b: Laxfisket och smalaxfangsten i Ostersjrin. Vandr. fiskudr. Medd. 13.<br />
[Salmon fl -shely and capture of small salmon in Ostersj'M]<br />
— 1956-1961: Laxfisket i Ostersjtiomradet under senaste aren, ibidem 1956- 1961.<br />
L3almon fisnery In the region of nsterse in recent years1<br />
— 1958: Seasonal fluctuations in the catches of Salmon in the Baltic. Journ. d. Cons., Vol.<br />
23, 3. -<br />
13AHR, K., 1935a: Die Neukuhrener Forellenmarkierungen in den Jahren 1930-34. Ber. DWK<br />
• 7, 4.<br />
[Tagging of trout at Eeukuhren in the years 1930 to 1934]<br />
— 19356: Was fressen unsere Ostseelachse? Dtsch, Fischwirtsch. 1935. H. 52.<br />
[What do our Baltic Sea salmon eatT]<br />
- 223 -<br />
— 1936a: Die Neukuhrener Lachsfisdierei w.ihrend der Fangzeiten 1931/32-1933;34. Dtsch.<br />
Fischwirtsch. 1936, H. 24.<br />
[The salmor fishery during the fishing seasons 1952/32 to 1533/34<br />
Neukuhren1<br />
— 19366: Uniersudtungen über den Lachs IV, Nahrungs- und Gonadenubtersuchungen bei<br />
ostpreuflischen Treibnetzladisen. Z. f. Fisch. 345.<br />
[Investigations of the salmon. IV, Food examination and gOnad investigation<br />
in East Prussian salmon caught in driftnets1<br />
BARRINGTON, E. J. W., 1957: The alimentary canal and digestion, in M. E. BRowN..Physiology<br />
of Fishes, New York, 1957.<br />
BELDING, D. L.; and PRÉroNTAINE, G., 1961: A report on the Salmon of the north shore of the<br />
Gulf of St:Lawrence and of the northe:istern coast of Newfoundland. Contr. Dptmt. Fish., .<br />
No. 82.<br />
BENECK.E, B. ; 1881: Fische, FisCherei und Fischzucht in Ost- und WestpreuGen. Künigsberg,<br />
[Fish, fishery and fish rearing in East and West Prussia]<br />
. ,BERG, L. S., 1958: System der recenten und fossilen Fischartigen und Fische. Berlin, 1958.<br />
[System or the recent and fossil fish- like animais and fish]<br />
BERGERON, J., 1962..BibliDglaphiC . du Saumon de l'Atlantique. Min. Chass. Pêches, Quebec,<br />
No. 88.<br />
[Bibliography of the Atlantic salmon]<br />
BERNER, M., und ANWAND, K., 1963: Die Fangpliitze der südlichen Ostsee und ihre fischerei-<br />
liche Bedeutung 1956-1960 im Vérgleich zu 1953-1955. Z. f. Fisch. 11/1,2,1962-1963. •<br />
[The fishing grounds of the southern Baltic Sea and their importance for<br />
the fishery in 1956 to 1960 in comparison with 1953 to 1955]<br />
BEVERTON, R. J., and Hour, S. J., 1957: On the Dynamics o .f Exploited Fish Populations. H.<br />
Maj. Stat. Off., London, 1957.<br />
BLAIR, A. A., -1955: Atlantic Salmon tagged in east coast Newfoundland waters at Bonavista.<br />
J. Fish. Res. Bd. Canada, Vol. 13/2.<br />
BoLsTER, G. C., 1962: The influence of wind and tide on catch by drill nets. J. du Cons.,<br />
Vol. 27/2.<br />
at
•<br />
- 224-<br />
BRANDT, A. y. , 1959: Fanggerate der Kutter- und Kustenfisdierei. AID, 11Li-1 113.<br />
[Fishine . gear of the fishery by cItter ann of the coastal fishery]<br />
BRANDTNER, p., 1938: UtitermIchungen liber den Lachs V. Z. f. Fist-h., 36.<br />
[investigation: of the salmon]<br />
BRUFT, J. B., and Gitoo.r, C., 1963: Some aspects of olfactory and visual responses in Pacific<br />
Salmon. J. Fish lies. Bd: Canada, Vol. 20/2.<br />
BROWN, 1957: Experithental studies on Growth, in M. E. BROWN. Physiologv of Fishes,<br />
. New York, 1957.<br />
13OCKNIANN: A., 1929: Die Merhodik fischereibiologischer Untersuchungen an Meereslischen.<br />
Handb Rio! . A rb. . , AI''. 9, Tell 6 1,1929.<br />
•<br />
IThe methodology of fishery - biological investigations of sea fish]<br />
CARI IN, B , 195 1 : ovv:r lax.ens rommâng. Vandr. Fisk. Udr. Medd. 6.1951.<br />
L'Investigatons of the amount . of roe in the salmon]<br />
-- 1955: T4gIng of .S,Imon smolts in the river Lagan. Inst. Freshw. Res. Drottningholm, 36<br />
Result , of S dmori smolts t ,gging in the Baltic area. Rap. Proc. Verb., Vol. 147<br />
— 1959b: Salmon ,_onservat ion in the Baltic III (1). Rap. Proc. Verb., Vol. 148<br />
-- 1962a: Svnpunkter pa fragan urn Ostersjiins laxbestànd i belysning av de svenIsa ni irk-<br />
La?: forsk. nst. Medd. 5 1962.<br />
[Views on the question of the stock of salmon in terse and information<br />
on the :;wenirh experiments of tagging salmon]<br />
NEirist lax àtertâng d vid Grindand. t.axforsk. Inst. Medd. 8;1962.<br />
',Tagpen sa.lmon recovered in Greenland]<br />
- 1963: La forskninginstitmet och dess luttiilsvarande verksamhet. La x forsk . Inst. NI ed. 7-81963.<br />
Li<br />
.nstitute for Salmon Research and its activities'<br />
och .lonv.s.,0>, K. B., 1937: Blanklaxmârkning pa Norrbottenkusten. Norrb. Landm, RI<br />
LTagin 02 . I .ree, salmon on the coast of 1\iorrbotterl<br />
cmos I.NSF N, O., 1961a: Untlersogel,‘r over Dan.li.t ■efanpter 1 t. 1 ersoe!. I sk 1.ndvr sog. 21/1961.<br />
LInvestigations of banish salmon captures In th bal tic Sea]<br />
- 1961b: Piscliminary results of an investigation on the food of Ralti.: Sahnon. 1CTS. ■ I 1961 93.<br />
— 1961-1963: The Danish Salmon Fishers ni the Eastern 13altic ibidem 1961 2, l'eh2, 10C, 1963/40. .<br />
— 1963: Del- Danske laxefiskeri i Ostersoen i seasonen 1962/63. Damn. Fisk. amlers., Mskr.<br />
[The Danish Salmon fishery in the Baltic Sea n the season 19 6 2/3]<br />
— and Tin.:Row, F., 1964:. Report .on population dynamics in Isaitic Salmon. It ! ".•<br />
1964 .46.<br />
CifitzAN, F., 1959a: Notes regarding Polish Salmon and Sea Trout Hsi-lei-1es in die se,,vons<br />
1955-1959. ICES, CM 1959/30.<br />
- 1959b: Lachs und Meerforelle in den polnischen Ostseefângen der J dire 1945-1955. Morsk.<br />
I list. Rybatity, 10;A, 1959 (polnisch).<br />
L-'almon and sea. trout in the Polish captures in the Baltic Sea in the<br />
years 1945 tb 19551<br />
— 1960: Results of investigations on the food of the Salmon and Sea Trout otf the Polish, •<br />
• Baltie coasts. ICES, CM 1960/70.<br />
DIXON, B., 1931: The age and growth of Salmon caught in the Polish Baltic. J. d. Cons., 6/3.<br />
1934: The àge and growth of Salmon caught in the 'Polish Baltic in the years 1931-1933.<br />
J. d. Cons., 9/1.<br />
EICIII.LBAUM, 1916: Reife und Nahrung von eingesandtén Lachsen. Rap. Prue. Verb., 23 (2), 1 -116.<br />
fMaturity and-food of salmon submitted]<br />
- Eu RENBAUM, E., 1936: Naturgeschichte und. wirtschaftliche Bedeutung der Seefische •Nord•-<br />
,europas. Handb. Seef. Nordeuropas, 2/1936.<br />
[1iatural histo•y and economical importance of sea fish of northern Europe]<br />
[p. 368]
ELSON, P. F., 1962: Predator-prey relationships between fish eating .birds and Atlantic Salmon.<br />
J. Fish. Res. Bd. Canada, Bull. 133. .<br />
ELWERTOWSKI, J., 1959: State of the southern Baltic.Sprat stodt in 1959. ICES, CM 1959/25.<br />
1964: The influence of the 1956 and 1963 winter season on the life of the southern Baltic<br />
. Sprat. Ibidem 1964/75.<br />
Fitrrscx, A., 1893: Der Elblachs. Prag, 1893.<br />
[The salmon of the Elbe]<br />
GEsNER, C., 1558: Historiae animalium liber III qui<br />
natura. Tig.uri, 1558.<br />
[Histories of animals, Book /II,<br />
GISLER, N., 1751: Rijn om Laxens natur odi fiskande<br />
- Vet. Acad. Handl., 1751-1752,6 Aufsâtze:<br />
[Investigation of the nature and<br />
Norrland] (six papers)<br />
est de piscium et aquatilium animantium<br />
— 225—<br />
which is of fishes and aquatic animals]<br />
i de Norrlândske Alfvarna. Kg!. Svensk.<br />
fishery of the salmon in the rivers of .<br />
GLOWINSKA, A., 1961: Polish observations in the southern Baltic, Jan. 1960–June 1961. ICES,<br />
CM 1961/36.<br />
HAGMANN, N., 1938: The variations in the catch of Salmon and the water levels of the rivers.<br />
• Zool. Bot. Vanamo, Ann. Zool., 5 (6), 1-45. •<br />
Soc.<br />
HALME, E., 1961: Report on Salmon tagged in Finland. ICES, CM 1961/17.<br />
HALSBAND, E., 1953: Untersuchungen über das Verhalten von Forelle (Trotta iridea) und<br />
Di:1)d (Squalius cephalus) bel Einwirkung verschiedener Auflenfaktoren. Z. f. Pis& N. F.,<br />
. 2, H. 3/4,1953.<br />
[Investigations of the behaviour of trout (Trutta iridea) and of chub<br />
(Squalius cephalus) under the influence of various external factors]<br />
HASLER, A. D., 1954: Odour perception and orientation in fishes. J. Fish. Res. Bd. Canada,<br />
Vol. 11/2.<br />
— 1960: Homing.orientation in migrating fishes. Ergebn. Biol. 23.<br />
HAYES, F. R., 1949: The growth, general chemistry. and temperature relations of salmonid eggs.<br />
.Quart. Rev. Bio t ., Vol. 24/4.<br />
HEMPEL, G., und SAHRHAGE, D., 1961: Neuere Modellvorstellungen über die Dynamik genutzter<br />
Fisdlestânde. Ber. DWK, 16/2.<br />
[Newer model.coilceptions of the dynamics of expleitod fish stocks]<br />
HENKING, H., und FISCHER, E., 1905: Obersicht über die Seefischerei Deutschlands in den Gewâssern<br />
der Ostsee. Pub!. d. Cire., No. 13 B.<br />
[Survey of> tLp Gprmnn-p.r.n fiRhpvu in Abe% wmfnrc: nt tile —Ridtie Sea]<br />
HENKING, H., 1913: Die Lachsfrage im Ostseegebiet I. Rap. Proc. Verb., 16/6,1-65.<br />
— 1916: Die Lachsfrage im Ostseegebiet II. Rap. Proc. Verb., 23/2,1-116."<br />
Line saimpn Toeston in the region or the baltic<br />
— 1929: Untersuchungen an Salmoniden. Ibidem, Vol. 61. •<br />
[Investigations on salmonids)<br />
1931: Untersuchungen an Salmoniden, 2. T. Ibidem, Vol. 73.<br />
[Investigations on salmonids, second part l<br />
. _<br />
HicxLING, C. F., and RUTENBERG, E., 1936: Tue ovary as an indicator of the spawning period<br />
_ in,fishes. J. Mar. Biol. Ass. U. K., Vol. 21.<br />
HOAR, W. S., 1957: Endocrine organs (in M. E. BROWN, Physiolugy of Fishes, 1957). Acad.<br />
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HUNTSMAN, A. G., 1941: Cyclical aimndance and birds versus Salmon. J. Fish..Res. Bd. Ca- •<br />
nada, 5/3.<br />
IntÉR, D. R., and 'BITNERS, J., 1959: Biochemical studies on Sockey-Salmon during spawning<br />
. migration, Cholesterol, Fat, Protein and Water in .the body of the standard fish. J. Fish.<br />
Res. Bd. Canada, Vol. 16/2. •
- 226 -<br />
Paw, T. H., 1938: Fluctuations in the Baltic stock of Salmon, 1921-35. Rap. Proc. Verb., Vol.<br />
106.<br />
— 1948: On the periodicity of Salmon reproduction in the northern Baltic area and its causes.<br />
Rap. Proc. Verb., Vol. 116.<br />
— 1958: Ober die Lachsertrâge im Oulujoki in den Jahren 1870-1948. Acta Zool. Fenn., 94: •<br />
[On the yields of salmon in the Oulujoki in the years 1870to 190]<br />
— and MENZIES, W. J. M., 1936: The interpretation of the zones on scales of Salmon, Sea<br />
Trout and Brown Trout. Rap. I>roc. Verb., Vol. 97.<br />
JOKIEL, J., 1958: Los6s (Salmo salar) Rzeki wisli, Roczniki Nauk Rolniczych, Tom 73-B-2.<br />
The. ALI a vt-1-:c s in,.) u I r ;ref LS<br />
fri b i4-,- /es. Yr 6tDC,k •,011. 115h 54j 4,e. Vo!. "13 - 3-2.<br />
KÂNDLER, R., 1958:. Vorschlâge zur Erhaltung des Ladisbestandes in der Ostsee. Fischwirtsch.<br />
1954/2.<br />
LPropositions . for the preservatiOn . Of . the stocks of salmon in the Baltic<br />
Sea] •<br />
— 1.955: Zut: gegenwârtigen Lage der Lachsfistherei in dir Ostsee. FischerbL 1955/10.<br />
•<br />
[ On . the present •status of the salmon fishery In tne Baltic Sea]<br />
— 1958: Ergebnisse schwedischer Ladismarkierungen in der Ostsee nadi Wiederfângen deutscher<br />
Fischer. Fischerblatt 1958/5.<br />
[Results of the SI;iedish tagging of salmon in the Laitic Sea on hand of<br />
recaptures by German fishermen]<br />
—.1958-1963: The German Salmon fishery in the south-eastern Baltic ... ICES, CM 1958/40,<br />
1959/33, 1961/23, 1962/5, 1963/31.<br />
— 1959-1963: Gerinan Salmon fishery in the Baltic Ann. Biol., 14/210-211, 15/217-219,<br />
16/249-257, 17/238-240, 18/204-205.<br />
— und Lill-MANN, M., 1957: Ober den Lachsbestand und die Ertrâge des deutschen Lachsfanges<br />
in der südtistl. Ostsee. Ber. DWK, 1413.<br />
[On the stocks of -salmon and the yields of the German salmon catches in<br />
the southeastern Baltic Sea]<br />
« KOCH, H., BERGSTROM; E., and EVANS, J., 1964: Studie on the physiological variabilite of the<br />
Salmon. Laxforskn. Inst. Medd., 1964/1.<br />
LARSEN, K.,.1955: Fish population analyses in soine small Danish Trout streams by means of •<br />
D. C. elect'ro-fishing. Medd. Danm. Fisk. Havunders., N. S. 1/10.<br />
LINDROTH, A., 1950: Laxbestândets Fluktuationer i de Norlândska âlvarna..Sv. Vattenkr.<br />
Ftiren. Publ.; 415, 1950 15. -<br />
[l.luctuation of the stocks of salmon in the rivers of Dorrland]<br />
— 1952: Rommângden hos Indalsâlvens lax. Vandr. Fiskundr. Medd. 6. •<br />
IAmounts of roe jn the salmon of lndalsgivj<br />
— 1955a: Mergansers as Salmon and Trout predators in the River Indalsalvem Rep. Inst.<br />
Fr. Wat. Res. Drottningholm, 36.<br />
— 1956: Laxodlingsprogrammet for det nârmaste Decenniet. Vatt. ftir. Publ. 460, 1956/9.<br />
[Program for rearing salmon durin the next deCadel<br />
— 1957: Baltic Salmon fluctuations: A reply. Inst. Fr. Wat. Res. Drottnh., 38.<br />
— 1961a: On growth fluctuations in Baltic Salmon. ICES, CM 1961/7:<br />
— 1961b: Sea food of Baltic Salmon smolt. Ibidem 1961.8. •<br />
— 1962: Baltic Salmon fluctuations 2: Porpoise and Salmon. Inst. Fr. \Vat. Res. Drottningholm,<br />
44. •<br />
— 1963: The body/scale relationship in Atlantic Salmon, a preliminary report. J. d. Cons.,<br />
Vol. 28/1.<br />
LISHEV, M. N., 1958: DitTerences• in the structure: of scales of Baltic • Salmon of various river<br />
populations. ICES, CM 195864.<br />
[ P. 369]
- 227-<br />
— 1961: Einige Gesetzmaffigkeiten der Popula.tionsdynamik des Ostseelachses (russisch). Issl.<br />
Inst. Rybn. Akad. N AUK, Leu. SSR, Riga.<br />
[Some regularities of the population dynamics of the salmon of the Baltic<br />
Sea] (in Russian)<br />
MAHLEE, J., und Ilmeru Nu, G., 19.63: Gestehungskosten und Betriebserfolg der Ostsee-FIodisee-<br />
Kutterfischerei. Fischerbl. 1963.7.<br />
[Working costs and operational success of the Baltic Sea / high sea<br />
fishery with cutters]<br />
MAEDA, H., 1953: Ecological analyses of pelagic shoals I. Bull. Jap. Soc. Scient. Fish. Vol. 19.4.<br />
N1ENZILS, W. J. M., 1925: The Salmon. W. Blackwood, Edinburgh/London, 1925. ,<br />
MEYER-WAARDEN, P. F., 1938: Attssetzungen von Regenbogenforellen in die Ostsee. Ber<br />
Deutsch. Wiss. Korn. f. Meeresforschg, (DWK), N. F. 9/2<br />
[Relertses'of rainbow trout in the Baltic Sea]<br />
1939: Versudre mit Aussetzungen von Bach- und Regenbogenforellen in die westl. Ostsec<br />
Rap. Pro.:. Verb., 109.13.<br />
[Trials with releases of brook trout and rainbow trout in the western<br />
Baltic Sea]<br />
•<br />
— 1942: Dic 7eesenfischerei auf Hering und Sprott, ihre 4'ntwicklun g und Bedcutiang fi:r the<br />
Ostseefischerei und ihre Auswirkungen auf den Blankfischbestand der Ostsee. I sch.,<br />
40/4-5. [P.<br />
lThe fishery for herring and sprat, its development and importance for the<br />
fishery in the Baltic Sea and its effect on the open stock of fish in the<br />
Baltic Sea]<br />
MITANS, A., 1963: Studies on the feeding habit of Salmon parrs in the Latvian rivers, NISlir.<br />
MORGAN, N. C., and WADDELL, A. B., 1961: Insect emergence from a small TYOUt 10(11 and its<br />
bearing on the food supply of fish. Freshw. Salm. Fish. Res., 25.<br />
MUIR, S., and.WHITE, H., 1963: Application of the Paloheimo linear equation for estimating<br />
mortalities to a seasonal fishery. J. Fish. Res. Bd. Can., 20/3.<br />
NERESHEIMER, E., 1941: Die Lachsartigen. Handb. Binnenf., IIIA, 1941.<br />
[The salmonicIF1<br />
NIELSEN, J., 1961:Contributions to the Biology of the Salmonidae in Greenland. MedeGronland<br />
Fisk. Unders., 159/8.<br />
Nutor.sxr, G. W., 1957: Spezielle Fischkunde, Berlin.<br />
[Special fish science]<br />
NoaDQutsr, 0., 1908: Die Lângenrnafle von in der siidlichen Ostsee g,etangenen Ladisen und<br />
Meerforellen ais Vorbereitung einer eventuellen Einführung von vereinbarten. MindestmaSen<br />
dieser Fische. Rap. Proc. Verb., Vol. 9.<br />
[The length measurements of salmon and seà trout caught in the southern<br />
Baltic Sea, as preparation for the eventual introduction of conventional<br />
minimum measurements for these fish]<br />
— 1924: Times .of entering of the Atlantic Salmon in ;he rivers. Rap. Proc. Verb., Vol'. 33.<br />
OTTERSTRÔM, C. V., 1933: Reife Lachse in Teichen. J. d. Cons., Vol. 8.<br />
[Mature salmon in ponds]<br />
OSTERDAHL, L., 1963: Tre . ars smoltutvandring i Ridclen. Laxforskn. Inst. Med., 10. '<br />
[Three years of smolt migration in Ricklegn;<br />
PALOHEIMO, J. E., 1961: Studies on estimation of mortalitieS I, Ctirnparison of a method descri-<br />
bed by Beverton and Holt and •a new linear Formula. J. Fish. Res. Bd. Canada, 18 (5).<br />
PIGGINS, D. J., 1958: Investigatio n. on predators of salmon smolts and parr. Salmon Res. Tr:<br />
Ireland, 5, Dec. 1958: •<br />
---: 1962: Some preliminary results of feeding thyroid material to salmon pa'rr. ICES, CM<br />
1962/2.<br />
•
- 228-<br />
PETERSEN, C. G. .11, and OrrEas -rxeim, A., 1904: Die Ostseefischerei in ihrer jetzigen Lage;<br />
I. Obersicht über die dânischen Gewasser innerhalb Skagens. Pub!. d. Circonst., 13 A.<br />
LThe fishery in the Baltic Sea in its present Ftate. I. Survey of the<br />
Danish waters inside Skagen]<br />
POPE, J. A., MILLs, O. H., and SHEARER, W. M., - 1961: The fecundity of Atlantic Salmon.<br />
Salmon Freshw. Fish. Res.,•29.<br />
PYEFINCH, K. A., 1955: A review of the literature on the Biology of . the Atlantic Salmon.<br />
Freshw. Salmon Fish. Res., 9.<br />
PIECHURA, J., 1961: Température et Salinité des eaux de la Baltique méridional août 1960 -<br />
Mai 1961. ICES, CM 1961/68.<br />
[Temperature and salinity of the waters of the southern Baltic Sea in<br />
Augupt 1960 to May 1961]<br />
SANDMANN, J. A., 1906: Obersicht über die Scefischerei Finnlands. Pub!. d. Circonst., 13 C.<br />
[Y.,urvey of the Finnish sea fishery]<br />
SCHEURING, L., 1929: Die Wanderungen der Fische. Ergebn. Biol., 5.<br />
[The migrations of fish] •<br />
. SCHRÂDER, T. H., 1928: Die erste fiatürliche Nahrung ausgesetzter Bachforellenbrut. Z. f:<br />
' Fisch., 26.<br />
[The first natural food of liberated fry of brook trout]<br />
SHAw, J., 1836: An account of sonie experiments and observations on the parr and ova of the<br />
salmon, proving the parr to be the young of the Salmon. Edinburgh, New Phil. J., 21.<br />
- - 1838: Experiments on the development and groWth of the fry of the Salmon from the<br />
exélusion of the ovum to the age of 7 months. Ibid., 24.<br />
SJÔGREN, S. J., 1962 und 1963. Det svenska laxfisket i Ostersjbomradet. Laxforsk. Inst„ Medd.,<br />
1962/9, 1963/6.<br />
[The Swecish ralmon fishery in the region of bsterse]<br />
SUWOROW, J. K., 1959: Allgemeine Fischkunde. Berlin, 1959:<br />
[General f s'n science]<br />
SVÂRDSON, G., 1949: Natural selection and eg•g number in fish.. Inst. Freshw. Res. Drottningh.<br />
Rep., 29.<br />
— 1955: Salmon stock fluctuations in the Baltic sea. Inst. Freshw. Res. Drottningh. Rep., 36.<br />
— 1957: Laxen och klimatet. Ibidem, 38.<br />
[Salmon and climate]<br />
SZATYBELRO,. M., 1957: Studies of factors influencing catching potential of Salmon and Trout:<br />
fishing gear. Morsk. Inst. 1957/9.<br />
• THukolisr, F., 1959: Die Entwicklung der deutschen Lachstreibfietzfisdierei und die Erprobung<br />
neuèr Treibnetze. Fisdierbl., 1959/9.<br />
[The development of the German salmon fishery with driftnets and the<br />
testing of new driftnets]<br />
— 1960: Untersuchungen über Bestandsfluktuationen beim Ostseeladis. Ber. DWK, 16/1.<br />
[Investigations of fluctuations in the stocks Of the salmon of the Baltic<br />
Seal<br />
— 1962: Ober Qualitâtsschwankungen und die Bedeutung der Fettspeidierung beim Ostsee- •<br />
lachs. Arch. f. Fisch. Wiss., 13/1-2. .<br />
[On fluctuations in the quality of Baltic Sea salmon and the iMportance<br />
of the fat accumulation in the Baltic Sea salmon'<br />
— 1964: . Die Selektionswirkung von Angelhaken in •dei : Lachstreibleinenfischerei. Ibidem, 1964:<br />
• 1-1.2.<br />
. . . •<br />
[The selective effect of hooks in the driftline.fishery for salmon]
- 229-<br />
TRYBOM, F., und WOLLEBACK, A., 1904: Obersicht über die Seefisdierei Schwedens an den südlidien<br />
und iistlichen Küsten dieses Landes. Publ , Circ., 13 A.<br />
[Survey of the sea fishery of Sweden on the southern and eastern coasts<br />
of thiS country]<br />
— 1910: Bericht über die Aufzucht, Markicrung und den .Fang von Lachsen und Meerforellen<br />
[ 1). 371]<br />
im Ostseegebiet wâhrend der Jahre 1904-1908. Rap. Proc. Verb., Vol. 12/6.<br />
[Report on the rearing, tagging and the capture of salmon and sea trout<br />
in the region of the Baltic Sea in the years 1904 to 1908]<br />
TWOMEY, E., and RIORDAN, A. 0., 1963: Novements of Salmon around Ireland, IX. Proc.<br />
Royal Ir. Akad., Vol. 93 B 5.<br />
VLADHLOV, V. D., 1956: Fecundity of Wild Speckled Trout (Salvelinus fontinalis) in Quebec<br />
lakes. J. Fish. Res. Bd. Canada, 13/5.<br />
WENT, A. E. J.; 1956: The Irish drift net fishery for Salmon. J. Dptrnt. Agr., Vol. 52.<br />
— 1964: Irish Salmon, a review of investigations up to 1963. Scient. Proc. Royal Dubl. Soc.,<br />
Ser. A, Vol. 1/15.<br />
WHITE, H. C., 1936: The food of Kingfishers and Mergansers on the Margeree river, Nova<br />
Scotia. J. Fish. Res. Bd. Canada, 2/3.<br />
— 1937: The food of Salmon fry in eastern Canada. J. Fish. Res. Bd. Canada, 2/5.<br />
— 1939: Factors influencing descent of Atlantic Salmon smolts, Nova Scotia. J. Fish. Res. Bd.<br />
Canada, 415.<br />
WISBY, W. J., and HASLER, A. D., 1954: Effect of olfactory occlusion in migrating Silver Salmon.<br />
J. Fish. Res. Bd. Canada, 11/4.<br />
Wn.LER, A., und QUEDNAU, W., 1931: Untersuchungen über den Ladis (Salmo salar L.). Z. f.<br />
Fisch., 29.<br />
[Investigations of the salmon (Salmo salar L.)]
Table I. Captures per unit effort with driftlines under different wind directions and wind<br />
Speeds for the months November to March inclusive.<br />
Wind •<br />
•Season Month<br />
5 Beaufort >5 Beaufort To tal<br />
E Calm Average S W E Aver. mean<br />
• XI 16,1 18,9 . 23,9 22,2 20,3 14,4 24,5 19,5 20<br />
XII 17,2 7,8 3,3 9,4 14,7 14,7 12<br />
1954/55 I 13,9 16,1 3,3 11,1 20,0 13,4 5,6 13,0 12<br />
II 12,2 4,4 8,9 8,5 9<br />
III 18,9 13,0 5,6 17,4 3,3 11,6 12<br />
XI 7,8 7,5 7,0 16,0 4,0 8,5 12,0 7,0 7,0 8,7 9<br />
XII 8,0 4,5 3,0 5,2 19,5 10,7 6,8 12,3 9<br />
1955/56 I - 6,2 5,9 6,3 5,5 4,5 S 5,7 7,9 4,5 4,0 5,5 6<br />
II<br />
III 10,5 18,2 21,1 16,5 1 34,4 49,2 21,4 35,1 1<br />
XI 20,7 11,9 25,6 14,1 29,6 20,4 12,5 27,0 30,3 23,2 21,8<br />
XII 19,6 29,7 15,8 30,8 23,9 22,8 35,2 13,3 23,7 23,8<br />
1956/57 I .10,0 27,5 27,8 7,3 12,7 17,1 46,5 26,3 36,4 26,8<br />
II 5,0 6,6 12,5 21,0 6,5 10,3 45,5 15,0 30,3 20,3<br />
III 14,2 20,3 77,5 16,5 5,6 26,8 36,6 23,4 31,5 20,2 27,9 27,4<br />
XI . 8,9 9,5 17,9 11,0 11,6 10,5 9,5 16,7 12,2 11,9<br />
XII 12,5 13,4 5,3 15,4 11,6 11,7 4,1 19,7 13,9 29,9 16,9 14,3<br />
1957/58 I 14,0 5,5 17,3 6,1 9,6 10,5 19,3 8,8 35,2 25,3 22,1 16,3<br />
- II 3,9 9,4 7,5 3,7 3,7 5,6 1,6 10,7 5,4 5,0 5,7 5,7<br />
III 1,6 4,0 4,5 4,8 3,7 11,8 1,4 2,4 5,2 4,5<br />
13<br />
8<br />
24,0<br />
10,5<br />
tx.1<br />
1-1<br />
•<br />
f\.)<br />
o
X1 12,3 20,9 3,3 9,0 10,8 11,3 34,8 34,8 23,1<br />
XII 14,7 32,7 21,7 14,3 21,6 21,0 2, 1 46,2 34,7 18,8 30,7 25,9<br />
1958/59 I 9,9 12,1 18,9 21,8 21,5 16,9 33,0 34,7 25,0 30,9 23,9<br />
II 10,8 7,3 8,6 4,9 7,9 52,9 50,8 19,3 41,0 24,5<br />
- II I 2,1 15,4 17,7 5,8 • 10,2 (15)<br />
1959/60<br />
XI<br />
XII<br />
I<br />
II<br />
III<br />
7,9<br />
7,3<br />
12,5<br />
6,0<br />
9,1<br />
10,3<br />
8,6<br />
5,9<br />
7,7<br />
' 5,5<br />
1,8<br />
8,2<br />
10,5<br />
9,8<br />
5,7<br />
5,2<br />
•<br />
6,2<br />
7,2<br />
- 6,0<br />
8,5<br />
8,2<br />
8,2<br />
8,5<br />
5,6<br />
7,2<br />
12,2<br />
3,6<br />
11,5<br />
6,7<br />
5,5<br />
7,7<br />
13,0<br />
5,2<br />
12,1<br />
11,6<br />
8,4<br />
9,2<br />
8,8<br />
10,3<br />
11,6<br />
7,6<br />
9,5<br />
7,0<br />
22,5<br />
9,3<br />
9,9<br />
8,1<br />
7,6<br />
7,1<br />
.<br />
.<br />
.<br />
•<br />
.<br />
.<br />
' .<br />
•<br />
•<br />
.<br />
.<br />
•<br />
.<br />
1960/61<br />
" .<br />
•<br />
" .<br />
1961/62<br />
XI<br />
XII<br />
I<br />
II<br />
III<br />
XI<br />
XII<br />
I<br />
II<br />
III<br />
.<br />
9,4 15,1<br />
11,0 13,8<br />
17,8 11,1<br />
10,9 7,8<br />
3,4<br />
_<br />
13,5 . • 11,7<br />
19,0 23,2<br />
11,6 10,2<br />
14,4 12,6<br />
. 6,5 7,1<br />
•<br />
11,2 15,2<br />
12,1 13,8<br />
, .• 6,7<br />
4,9 . .<br />
• •<br />
10,7 -11,8<br />
22,0 • 12,1<br />
20,2 14,8<br />
. 11,2 5,9<br />
3,7 6,6 •<br />
•<br />
9,8<br />
4,3<br />
12,7<br />
12,1<br />
11,8<br />
9,3<br />
4,2<br />
10,4<br />
19,1<br />
14,2<br />
11,0<br />
6,0<br />
-<br />
11,5<br />
11,9. 13,9<br />
14,3 •<br />
8,6 -<br />
. 5,9<br />
,<br />
12,2 18,6<br />
29,9<br />
14,7 35,0<br />
22,5 . 31,1<br />
8,2<br />
-<br />
16,8<br />
13,9 8,2<br />
20,1<br />
.<br />
•<br />
'<br />
10,5 11,3<br />
37,6 15,8<br />
39,0 22,0.<br />
21,3 . 15,4<br />
5,3 5,8<br />
14,2<br />
11,9<br />
17,2 -<br />
8,6<br />
5,9<br />
13,2<br />
27,7<br />
27,7<br />
22,6<br />
6,4<br />
•<br />
.<br />
8,4<br />
13,5<br />
.12,0<br />
14,5<br />
9,0<br />
5,1 .<br />
10,8<br />
11,8<br />
23,4<br />
21,0<br />
16,8<br />
6,2<br />
- 15,8<br />
-<br />
1962;63 XI 9,9 9,8 7,9 9,6 16,1 10,7 10,3 - 8,4 8,3 9,3 9,1 9,9 -<br />
XII 7,3 9,1 9,3 6,5 2 , 4 6,9 10,2 9,4 9,8 8,4<br />
1 The values for March 1956 were left out of consideration when calculating the mean.<br />
The data are based on. short-period, very large catches, which should not be considered<br />
as measure for the strength of the stocks.<br />
2 Obtained with the aid of the average monthly course in Table 7.<br />
9,2<br />
8 2
Table II. Captures per unit effort under different wjnd directions and wind. speeds on all •<br />
fishing grounds for the months February to April inclusive.<br />
Wind .<br />
Season MOnth<br />
Beaufort >4 Beaufort<br />
W N E Calm Average S W N E Mean<br />
1955/56 IV 4,2 12,4 9,9 7,1 8,4 13,0 13,0<br />
1956/57 II 10,8 7,5 ' 9,1 6,7 8,5<br />
III 9,0 4,7 7,4 7,0<br />
- IV 4,3 6,7 5,3 11,1 6,9<br />
8,4" 13,0<br />
5,6 5,6<br />
8,3 • 4,4 • 6,4<br />
• • 5,0 0 2,5<br />
'<br />
.<br />
1957/58<br />
-<br />
II<br />
III<br />
IV<br />
6,3<br />
11,9<br />
8,1 .<br />
19,8<br />
3,8<br />
14,9<br />
11,8<br />
, ,<br />
5,3<br />
7,7<br />
8,5<br />
7,5<br />
5,8<br />
13,6<br />
8,1<br />
f<br />
3,0<br />
,<br />
4,1<br />
1,8<br />
4,8<br />
- 4,1 .<br />
2,4<br />
. .<br />
.<br />
9,2 3,3<br />
1958/59 II 43,3 7,7 8,4 . 22,4 20,5 3,2 - 3,7<br />
• III 13,7 13,6 19,0 9,7 14,0 8,3 8,3<br />
• IV • 4,4 3,6 5,2 4,2 10,0 5,5 • 2,9 - 2,9<br />
13,3 4,8<br />
1959/60 II 20,4 14,9 13,3 13,9 ' 15,6 7,0 3,0 10,6 6,9<br />
III 12,0 25,0 2,7 9,2 2,5 10,3 6,6 5,7 6,2<br />
• . IV 5,9 6,1 5,8 2,8 7,9 5,7 -<br />
2,6 i_( ,<br />
10,5 5,2<br />
1960/61 II 14,4 15,4 10,7 13,5 11,7 23,6 0,5 1 1,9 •<br />
- III . 4,9 14,0 4,4 7,8 6,6 1,7 4,2<br />
' IV 4,3 1,7 . 7,5 2,3 . 5,4 4,2 12,7 12,7<br />
8,5 9,6<br />
1961/62 H 13,1 . 18,1 13,4 ' 1,5 11,5 '8,7 12,1 10,9 10,6<br />
III 9,9 8,4 6,1 30,6 19,5 14,9 5,8 0,5 1,3 13,5 5,3<br />
IV 4 ' 3 5,2 0,6 • 1,0 7,3 3,7 2,6 0,5 1,7 8,5 3,3<br />
10,0 • 6,4<br />
1962/63 IV . 8,2 . 2,5 10,0 8,2 5,0 6,8 4,9 4,3 2,3 3,8<br />
6,8 3,8
Table III. Yields of salmon and sea trout in the entire<br />
Baltic Sea (without the riyers) in t. (For references<br />
. see 2.3.4.)<br />
ear Sweden Denm. Germ.* . Fini. Poland USSR Total<br />
1895 107 . - 69 243 214 633<br />
189 6. ' 41. 132 254 . 191. - 618<br />
1897 - 90 • 88 344 230 752<br />
1898 50 65 250 ' :237- 602<br />
1899 • 30 55 . 175' « 246 ,<br />
506<br />
1900 , 30 52 . 180 .. 154 , •<br />
- .416<br />
1901 . 10 • 55 . 230 56 ',. • 351 '<br />
1902 ''30 • 40 90 .51 • « 211<br />
1903 - 54 18 . .,i, . 70 ..• • 70' ' •<br />
• 210<br />
1904 ..,. 36 21 .• • 70 • - 75 • 202<br />
1905. , 42 ' • 23<br />
80- - 59 204<br />
1906 48 • 21. ' . . 80 92 • 241,<br />
1907 • 69 - ' 25. '43 • 307 444<br />
1908 . • 62 - . 38 • • 79 290 . . • 469 -<br />
1909 120 52 104 '. (350) 626<br />
1910 50 47 . 75 (250) 422 .<br />
1911 ' . 87 .40 . 30 . 111 . . . .<br />
268 -<br />
1912 ' 91 • 41 52 107 291<br />
1913 113 37 -, 83 117 ' 250<br />
1914 ' 170 42 78. . 108. .398"<br />
1915 173 • 66 47 . 152 . 43 8 •<br />
1916. • 124 -- 31 124 . 256• 536<br />
1117 176 ' 25 99 166 . 466<br />
1918 124 • ' 24 • ' 169 137 .454<br />
1919 240 - 78 • 108. (180) : 606<br />
1920 400 .. 88 68 '(250) 806<br />
1921, 425 . 85 • 43 . 245 43 841<br />
1922 , 297 - - 48 • 105 . 195 240 • 885<br />
192 3 • .288 44 ., - 93 184 87 . 696<br />
1924 . 203 • 19 64 228 71 .66L , 651<br />
1925' 160 - 44 68 ' 308 35 64L 679 .<br />
1926 212 60 151 244 - 115 73L 855<br />
1927 310 77 • .202 ' 316 173 - 88L 1166<br />
1928' 306 55 343 • 124 • • 259 . 147 - 1234<br />
1929 ' 206 . 33. 189 135 132 206 901<br />
1930 222 . 52 . 146' • . 180 . 236 . 214 1050<br />
1931 . 401 . 77 • 160 208 81156 1083<br />
1932 350 167 275 • 241 • 86 • 211 - 1330<br />
1933 . 327 . , 142 159 168 • 104 269 • 1169<br />
1934420- 64 - 193. 299 68 162 1206<br />
1935 • 417 71, .118 • 237 70 • 189 1102<br />
1936 350 62 100 • .177. 68 . 118 . 875 .<br />
1937 292 33 55 213 . 32 •178 803<br />
1938 '250 . 34 - - 66 183 • 57 174 • 764<br />
1939 . 287 41 '37 153 12' .144 674.<br />
1940 • 241 52 ' • (35) 162 62 . 517<br />
1941 .. 330 .82 . (30) 413 825<br />
1942 395 , 130 (40) . 403' 928<br />
1943 634 157 • (10) , 323 . 1114<br />
1944 757 147 224 • 1128<br />
1945 1290 162 - 244 11 1707<br />
1946 . 1521 ' .478 • • .475 . 279 79 . 2832<br />
1947 1273 . 628. 395 486. 161 2937<br />
1948 - • 1304 948 • 10 289 406 280 ) 3237<br />
1949 • 1175 8,43 , 68 260 286 185 2817<br />
1950 1470 1323 192 «• 399 367 155 39C6<br />
- 233 -<br />
[p. 375]
•<br />
Yea.r<br />
Sweden<br />
Continuation<br />
Table III.<br />
Year Sweden Debm. Germ. Fini. Poland USSR Total<br />
1951 1175 1099 136 352 128 151 3041<br />
1952. 858 1330 144 « 383 67 149 2931<br />
1953 472 754 ' 75 350 71 117 1839<br />
1954 551 976 112 300 145 96 2180<br />
1955 356 611 157 300 42 182 1648<br />
1956 730 963 287 300 197 128 2605<br />
1957 • 392 896 345 300 185 98 2216<br />
1958 335 898 194 300 204 100 2031<br />
1959 413 935 243 . 293 239 99 2222<br />
1960 501 . 1065 217 300 320 83 2486<br />
1961 561 1386 , ,345 250 193 (100) 2835<br />
1962 (380) 1175 218 341 . 293 (80) 2487<br />
Figures in 0 are estimated<br />
L = Latvia only<br />
Finland USSR Total<br />
Latvia (estimated)<br />
.Oulojoki Tot. only<br />
- 234 -<br />
Table IV. The yields of salmon and sea trout . in the river s.<br />
of the Baltic Sea in . t, annual averages.<br />
(For references see 2.3.4.)<br />
1905-1909 135 11 270<br />
1910-1914 ' 155 8 240<br />
1915-1919 . 148 • 12 290<br />
1920-1924 192 6 .<br />
310<br />
1925-1929 99 7 46 240<br />
1930-1934 100 11 51 240<br />
1935-1939 108 9 34 220'<br />
1940-1944 172 6 290<br />
1945-1949 471 17 54 690<br />
1950-1954 214 45 420<br />
1955-1959 123 29 • • 270<br />
1960-1962 151 • , ' 91 59 340<br />
[P. 376]
•<br />
P<br />
•<br />
Table V. The yield of sea trout in the entire Baltic Sea<br />
without the rivers in t.<br />
(For references see 2.3.4.)<br />
Total<br />
Year Sweden Denmarkl Germanyl Poland Finland a. USSR<br />
estimated<br />
1940 65 . 0 0 0 100<br />
1941 . 63 : 1 ' 0 . 0 • - 100<br />
1942 50.. 2', 0 - 0 - 100<br />
1943 42 , ' 2 ' 0 , 0 100<br />
1944 57 • 2 - ,0 - 0 100<br />
1945 .5/ .. 1 . 0 .; 0 100<br />
1946 47 • 10* t: ' 0. 66 160<br />
'<br />
1947<br />
1948 •<br />
'55 .<br />
56 ' *<br />
15 - - , 0<br />
18 ' ''''' 0.'<br />
'<br />
* .<br />
64<br />
60 '<br />
180<br />
200<br />
1949 • 73 15' • 1 47 190<br />
1950 66 - 25 .- • .2 • . ' 54 200<br />
1951 .<br />
1952<br />
98<br />
68<br />
- 20 1 46 230<br />
. '<br />
1953 .<br />
1954<br />
1955<br />
1956<br />
1957 ' .<br />
•<br />
-<br />
58<br />
67. .<br />
'60<br />
59 ,' . '<br />
52 • .<br />
- 25 •.<br />
15<br />
20 ,<br />
10'<br />
30<br />
20.<br />
1 •<br />
. 0 .<br />
• 1<br />
. 5<br />
10 •<br />
30. . .<br />
24<br />
47<br />
102<br />
26 * '•<br />
41<br />
52<br />
.<br />
.180<br />
180<br />
250<br />
180<br />
200<br />
220<br />
1958<br />
1959<br />
47'<br />
: 55 - .<br />
20<br />
30<br />
2<br />
. ' . 17<br />
'. 69<br />
160<br />
220<br />
320<br />
1960 ' 76 30 33 -. 256 • 450<br />
1961 25 ' - 25 '• 10 ' 142 ' ' 250<br />
1962 ' 30 10 - 7 239 • . 350<br />
lin part after random samples<br />
0 = less than 0.5 t<br />
- 235 -<br />
[P. 377]
Table VI. Ratio between fork le<br />
. Baltic Sea salmon<br />
o,bdiun g e . Fork length<br />
' cm<br />
r11111<br />
.<br />
- 236 -<br />
th and total length in the<br />
cf. 5.1.1.). .<br />
'i'oIalIgc Total length<br />
0 . 1 .2 3 4 6 . 7<br />
30 32,6 32,7 32,8' 32,9 33,0 3 3 ,1 33,2 33,3 33,4 33,5<br />
31 33,6 33,8 .. 33,9 .34,0, • 34,1', 34,2 34,3 34;4 34,5 34,6<br />
32 34,7 34,8 34,9; 35,0 35,1 35,2 35,3 35,4 35,5 35,6<br />
33 35,7 35,8 . 35,9 36,1 • 36,2 36,3 36,4 36,5 36,6 '36,7<br />
34 36,8 , 36,9 37,0• 37,1 . .37,2 37,3 37,4 37,5 37,6 37,7<br />
35 37,8 37,9 38,0 38,1 38,2 38,3 38,5 38,6 38,7 38,8<br />
36 • • 38,9 39,0 39,1 39,2 39,3 .. 39,4 . 39,5 39,6 39,7 39,8<br />
37 399 40,0 40,1 40,2 • 40,3 40,4 40,5 40,6 40,7 40,9<br />
38' • ' 41,0 441 41,2 41,3 . .41,4 41,5 • 41,6 41,7 41,8 41,9<br />
39 • 42,0 42,1 42;2 42,3 42,4 42,5 ' 42,6 42,7 42,8 42,9<br />
40 43,0 43,1 43,3 43,4 43,5 43,6 ' 43,7 43,8 . 43,9 44,0<br />
41 44,1 . • 44,2 44,3 44,4 44,5 44,6 44,7 44,8 44,9 , 45,0<br />
42 45,1 45;2' 45,3 45,4 . 45,5 45,7 45,8 45,9 46,0 46,1<br />
43 46,2 46,3 46,4 46,5 46,6 46,7 46,8 46,9 47,0 47,1<br />
44 47,2 47,3 . 47,4 47,5 • 47,6 47,7 47,8 48,0 48,1 48,2<br />
45 48,3 • 48,4 48,5 48,6 48,7 48,8 48,9 49,0 49,1 49,2<br />
46 49,3 49,4 • 49,5 . 49,6 .49,7 49,8 49,9 50,0 50,1 50,2<br />
47 5 .0,4 - 50,5 50,6 50,7 50,8 50,9 51,0 51,1 51,2 51,3<br />
48 51,4 • 51,5 51,6 51,7 51,8, 51,9 52,0 52,1 52,2 52,3<br />
49 52,4 . 52,5 52,6 52,8' 52,9 53,0 53,1 53,2 53,3 53,4<br />
50 • 53,5 53,6 • 53,7 53,8' 53,9 54,0 54,1 54,2 54,3 54,4<br />
-51 54,5 54,6 -54,7 54,8 54,9 55,1 55,2 55,3 55,4 55,5<br />
52 55,6 55,7 55,8 55,9 56,0 56,1 56,2 56,3 56,4 56,5<br />
53 56,6 56,7 56,8 56,9 57,0 57,1 57,2 57,3 57,5 • 57,6<br />
•54 57,7 . 57,8 57,9 • 58,0 58,1 58,2 58,3 • 58,4 58,5 • 58,6<br />
55 '58,7 -58,8 58,9 - 59,0• 59,1 • 59,2 59,3 59,4 59,5 • 59,6<br />
56 59,7 59,9 60,0 .60,1 60,2 60,3 60,4 60,5 60,6 60,7<br />
57 60,8 60,9 . 61,0 - 61,1 61,2 61,3 61,4 61,5 61,6 61,7<br />
58 61,8 61,9 - 62,0 62,2 . 62,3 62,4 62,5 62,6 62,7 . 62,8<br />
59 62,9 63,0 63,1 . 63,2 63,3 • 63,4 63,5 63,6 63,7 63,8<br />
60 63,9 64,0 64,1 64,2 64; 3 64,4 . 64,6 . 64,7 64,8 64,9<br />
61 65,0 • 65,1' 65,2 65,3 .65,4 • 65,5 • 65,6 • 65,7 65,8 65,9<br />
66,0 66,1: 66,2 66,3 66,4 66,5 66,6 66,7 66,8 67,0<br />
63 67,1 67,2 67,3 .67,4 67,5 67,6 67,7 67,8 67,9 68,0<br />
64 68,1 *68,2 68,3, -. 68,4 68,5 68,6 68,7 68,8 68;9 69,0<br />
65 69,1 69,3 69,4 • 69,5 69,6 69,7 69,8 69,9 70,0 70,1 •<br />
66 70,2 70,3 70,4 70,5 70,6 70,7 70,8 70,9 71,0 71,1<br />
67 111,2 71,3 71,4 . 71,5 - 71,7 71,8 71,9 . 72,0 72,1 72,2<br />
68 72,3 72,4 72,5 72,6 '.72,7 72,8 72,9 73,0 73,1 73,2<br />
69 - 73,3 • • 73;4 73,5 73,6 . 73,7 73,8 73,9 74,1 74,2 74,3<br />
. 74;4 74,5 74,6 74,7 74,8 74,9 75,0. 75,1 75,2 . 75,3<br />
71 75,4 75,5 - 75,6 75,7. • 75,8 . 75,9 '.76,0 . 76,1 76,2 , • 76,4<br />
• 72 . 76,5 76,6 • 76,7 76,8 76,9 77,0 77,1 77,2 77,3 • 77,4<br />
73 77,5 77,6 • 77,7 • 77,8 77,9 - 78,0 78,1 • 78,2 78,3 78,4<br />
74 . 78;5 •78,6 • 78,8 78,9 79,0 79,1. 79;2 79,3 79,4 . 79,5<br />
79,6 79,7 79,8 79,9 . 80,0 80,1 80,2 80,3 80,4 80,5<br />
76 80,6 80,7 80,8 . 80,9 81,0 81,2 81,3 81,4 81,5 81,6<br />
77 • • 81,7 81,8 81,9 82,0 82,1 • 82,3 82,3 82,4 82,5 • 82,6<br />
.78 82,7 - 82,8 82,9 83,0 83,1 83,2 83,3 . 83,5 83,6 83,7<br />
79 • 83;8. 83,9 84,0 84,1 84,2 84,3 . 84,4 84,5 84,6 84,7.<br />
. 80 84,8 84,9 . 85,0• 85,1 • 85,2 85,3 • 85,4 85,5 15,6 85,7<br />
81 85,9 86,0 86,1 86,2 .86,3 86,4 86,5 . 86,6 .86,7 , 86,8<br />
82 . • 86,9 87,0 87,1 87,2 . 87,3 87,4 • 87,5 87,6 87,7 :87,8<br />
•<br />
[P. 37 8 ] I
, •<br />
11111:<br />
•'''"''n'nrse Fork<br />
•<br />
'length<br />
• Continuation<br />
Table • VI<br />
111111 • •<br />
,,.,„-<br />
, - 0 1 2 3<br />
,<br />
c in • ''',, .<br />
•<br />
Tot4Iânge Total length<br />
5 6 7<br />
-. 237 -<br />
. 83 87.,9 88,0 .88,1 88,3 88,4 88,5 88,6 88,7 .. 88,8 .88,9<br />
84 89,0 89,1 • 89,2 89,3 89,4 89,5 89,6 89,7 89,8 89,9<br />
85 90,0 90,1 90,2 90,3 90,4 90,6 .90,7 . 90,8 90,9 91,0<br />
86 91,1 91,2 91,3 . 91,4 91,5 91,6 91,7. 91,8 91,9 92,0<br />
•87 92,1 92,2 . • 92,3 . 92,4 • 92,5. 92,6 92,7 928 93,0 . 93,1<br />
88 93,2 . 93,3 - 93,4 , 93,5 93,6 93,7 93,8 93,9 94,0 94,1<br />
. . 89 94,2 94,3 94,4 94,5 94,6 94,7 • 94,8 94,9 95,0 95,1<br />
90 95,2 95,4 95,5 '95,6- 95,7 95,8 95,9 96,0 96,1 96,2<br />
91 • • - 96,3 • 96,4 -96,5 96,6 96,7 96,8 • 96,9 97,0 • 97,1 • 97,2<br />
. 92 ... 973 97,4 97,5 •97,7 97,8 . 97,9 98,0 98,1 98,2 98,3<br />
93 98;4 98,5 .98,6. 98,7 '98,8 .98,9 99,0 99,1 99,2 99,3<br />
94 . • 99,4 99,5 2 • 99,6 99,7 99,8 - 99;9 100,0 100,2 . 100,3 '100,4<br />
95 100,5 100,6 100,7 .100,8 100,9 101,0 101,1 101,2 101,3 101,4<br />
96 101,5 • 101,e 101,7 101,8 - 101,9 . 102,0 102,1 102,3. 102,4 102,5<br />
97 102,6 102,7 102,8 .102,9 103,0 103,1 103,2 103,3 103,1 103,5<br />
98 103,6 .103,7 103,8 103,9 104,0 104,1 104,2 104,3 104,4 104,5<br />
99 . 104,6 104,7 104,9 105,0 105,1 105,2 105,3 105,4 105,5 105,6<br />
100 105,7 • 105,8 105,9 - 106;0 106,1 106,2 106,3 106,4 '106,5 106,6<br />
101 -106,7 106,8 106;9 - . 107,0 107,1 - 107,3 107,4 107,5 '107,6 107,7<br />
. 102 '107,8 107,9 108,0 108,1 108,2 108,3 .108,4 108,5 108,6 108,7<br />
103 108,8 108,9 109,0 .109,1 109,2 109,3 109,4 109,5 109,7 109,8<br />
. 104109,9 > 1 .10,0 110,1 ..110,2 110,3 110,4 110,5 110,6 110,7 110,8<br />
105 • 110,9 111,0 - 111,1 111,2 111,3 111,4 111,5 111,6 111,7 '111,8<br />
106 - 112,0 '112,1 112,2 112,3 112,4 112,5 112,6 112,7 112,8 112,9<br />
107 - 113,0 .‘ 113;1 113,2 113,3 113,4 113,5 113,6 113,7 113,8 113,9<br />
.108 114,0: - ,114,1 114,3 114,4 • 114,5 114,6;' 114,7 114,8 114,9 115,0<br />
109 • 115,1 115,2 115,3, : 115,4 >115,5 115,6 115,7 • • 115,8 115,9 116,0<br />
110 116,1 " 116,2 116,3 116,4 116,5 116,7 . 116,8 116,9 117,0 . 117,1<br />
111 117,2 117,3 117,4 • 117,5 117;6 117,7 117,8 117,9 118,0 .118,1<br />
112 118,2 118,3 . 118,4 . 118,5 118,6 118,7 118,8 • 118,9 119,1 119,2<br />
113 119,3« «. 119,4 . - 119,5 • 119,6 119,7 119,8 119,9 120,0 • 120,1 120,2<br />
« 114. .120,3 120,4 120;5 120,6 120,7 120,8 120,9 121,0 121,1 .121,2<br />
115 • 121,4. 121,5 121,6 121,7 121,8 121,9 .122,0 122,1 122,2 122,3 .<br />
116 122,4 122;5 .122,6' • 122,7 122,8 122,9 123,0 123,1 123,2 123,3<br />
117 123,4 123,5 123,6 123,8 .123,9 124,0 124,1 124,2 124,3 :124,4<br />
- 118 124,5 • 124,6 124,7 124,8 124,9 125,0 . 125,1 125,2 125,3 125,4<br />
• 119 . • 125,5 125,6 . 125,7 .125,8 125,9 126,0 126,2 126,3 126,4 126,5<br />
120 . 126,6. • 126,7 1 26,8: 126,9 127,0 ' 127,1 127,2 ..127,3 127,4 127,5<br />
• 121 127;6 • 127,7 127,8.« 127,9 128,0 128,1 .128,2 128,3 128,5 128,6<br />
122 128,7- 128,8 128,9 129,0 129,1; 129,2 129,3 129,4 • 129,5 129,6<br />
123129,7 129;8 129,9. 130,0 - 130,1 • 130,2 1.30,3 130,4 130,5 130,6<br />
124 • 130,7 130,9 131,0 131,1 131,2 .131,3 131,4 131,5 131,6- 131,7<br />
125 131,8. .<br />
[p. 379]