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RY
-istl No. XXX:
REPORT FOR 1921
LANCASHIRE SEA-FISHERIES LABORATORY
THE UNIVERSITY OF LIVERPOOL
SEA-FISH HATCHERY AT PIEL.
Dp
Proressor JAMES JOHNSTONE, D.Sc.
Honorary Director of the Scientific Work.
LIVERPOOL.
Printep By C. Trytine & Co., Lrp., 53 VictortA STREET
1922.
REPORT ON THE INVESTIGATIONS CARRIED ON
IN 1921 IN CONNECTION WITH THE LANCASHIRE
SEA-FISHERIES LABORATORY AT THE UNIVERSITY
OF LIVERPOOL, AND THE SEA-FISH HATCHERY
AT PIEL, NEAR BARROW.
EDITED BY
Proressorn JAMES JOHNSTONE, D.Sc.,
Honorary Director of the Scientific Work.
CONTENTS. PAGE
Introduction. Jas. Johnstone... Soe ees AOC 5c sa8 1
Classes and other Work at Piel. A. Scott doc 506 306 el 32
The Plaice Fisheries of the Irish Sea. Jas. Johnstone, W. Birtwistle
and W. C. Smith. (See separate contents) nbc 265 Sie 37
A Biometric Study of Irish Sea Herrings. W. Birtwistle and H. Mabel
Lewis ... ene wae wes nde HOS Sor bor LS)
Chemical Composition of the Mussel, Tables of Results. R.J. Daniel 205
Some Diseases and Parasites of Fishes. Jas. Johnstone sae Seon
Appendix: Report on Ribble Mussel Beds. W. Birtwistle ... At end
INTRODUCTION.
The greater part of this Report consists of a summary
and discussion of the results of two investigations that have
now been carried on for a number of years: these are (1) the
plaice research, commenced by the Committee in 1908 and then
continued during 1919-21 as part of the work done under a
special grant made by the Ministry of Agriculture and Fisheries,
and (2) the biometric investigation of herring races, begun in
1913 as part of an international research. We think it desirable
that these routine observations should now be suspended so
that it may be considered what are the results and what they
indicate. For the opportunity of publishing the complete
results of the plaice work we are indebted to the Development
Commissioners, who have kindly allowed us to spend the balance
remaining over from the grant made for directed fishery
research in the Irish Sea. In addition to these two series of
data there remain Mr. Scott’s numerous estimations of organisms
2
present in the fourteen years’ samples of plankton taken by
Professor Herdman at Port Erin. These data are also being
summarised and discussed, and it is hoped that the results
may be ready in another year. It cannot be doubted that
full consideration of the observations so far made will indicate
new and fruitful lines of investigation, and it is probably
inadvisable to continue working by purely routine methods
without some interval of close criticism.
The Plaice Report.
This consists of :-—
(1) A summary, brought up to date, of the measurements
of Irish Sea plaice, made on the various fishing
grounds, during the years 1908-1920, by the Officers
of the Committee.
(2) A complete summary of all the results of the plaice-
marking experiments made during the years 1906-
1913.
(3) A summary of the results of observations made on
board fishing vessels during the years 1919-1920.
This work was arranged/ by the Oceanography
Department as part of the scheme of “ Directed
Research in the Irish Sea.”
(4) A general discussion of all the results obtained made
from the practical administrative point of view.
The attitude taken up in the course of this work was that
of the need for restrictions on seasons and methods of fishing
should it appear that there is a progressive impoverishment
of the Irish Sea plaice fisheries. The conclusions made from
the work already done may be stated briefly (and rather
dogmatically in the meantime) :—
(1) Impoverishment of the Irish Sea Fishing Grounds.
Nothing in the results obtained suggests that there has
been such an impoverishment. There are ups and downs.
3
The causes of these fluctuations is an interesting, scientific
problem, and one which may be solved—given sufficient
resources for investigation.
(2) Effect of War-time Restrictions on the Fishery.
There is no evidence that the military restrictions, in
operation in the Irish Sea in the years 1914-1918, had any
observable effect on the abundance of the plaice there in
1919-1920.
(3) Size-limits for Plaice.
There is no evidence that a size-lmit for plaice that may
legally be landed would have any effect on the abundance of
commercially valuable plaice on the Irish Sea fishing grounds.
A word or two may be said about what we regard as
“evidence.” Jf the Irish Sea plaice grounds are being
impoverished by too much trawling ; 7f the military restrictions
of 1914-1918 led to an accumulation of plaice in the Irish Sea,
and ¢f a size-limit could be shown to be useful in preserving
the plaice grounds from impoverishment. Then the practical
outcome of these findings would be administrative restrictions.
These restrictions would create new legal offences, punishable
by fines or imprisonments.
Therefore the scientific evidence that would justify us in
making administrative restrictions and by-laws ought to be of
the same nature, or just as convincing as would be the evidence
required by the police courts for the conviction of a fisherman
who would infringe these by-laws. We know what is the
nature of the latter evidence, and we hold that the results
obtained from these investigations have not the same degree
of strength and ought not to be used for the establishment of
new legal offences.
But the results that have been obtained may be strong
enough to justify a fishery authority in spending money on what
may be called fishery development. We do not say that it is
+
because we do not know that any schemes of development are
in contemplation. Also if a period of much greater exploitation
of the fishing grounds should come about in the near future—
say, as the result of a condition of severe food shortage—then
the results that we give here will make it all the easier to find
the point at which we may be taking more from the fishing
grounds than the recuperative powers of the latter can stand.
But we hope that the tendency of these investigations, and those
others that they suggest, will be in the direction of culture
vand development.
The Natural History Results.
From the point of view of general marine biology the
results indicated in the report raise very curious and fascinating
(and perhaps economically significant) problems. The shallow
sea off the Lancashire and Cheshire coasts, and the foreshore
there, may be rather unattractive to the zoologist. The
foreshore is mostly sand and mud; there is much pollution
from the adjacent cultivated and densely populated land area,
and the fauna and flora are commonplace from the point of
view of the naturalist collector. But the entire region is one
of extraordinarily high production because most of the organic
matter, in the form of foodstuffs, that is consumed in the
densely populated country draining into the Irish Sea off the
coasts of Cumberland, Lancashire and Cheshire 7s again
converted into organic matter. This enormous production of
proteid, fat and carbohydrate that goes on in the sea, entirely
from waste materials, is almost wholly beyond human control.
Only in the case of the mussel transplantation experiments,
made at Morecambe by the Committee, has there been any
attempt at utilising this production from waste matters. The
question of how still further to make use of the surplus pro-
duction of the sea may well become one of prime importance
in the future, and what appear now to be perfectly abstruse
problems of pure marine biology may require to be studied
5
in order that we may usefully control these powers of production
of organic substance. Many things that are apparent in present
economic tendencies suggest that this control over the regenera-
tive power of the littoral seas simply must be acquired.
The conditions that we speak of result in a shallow sea
densely crowded with marine organisms that have little or no
economic value : mussels, cockles, and shellfish that are mostly
unutilised ; small plaice, dabs, flounders, solenettes, sprats,
etc., that are not caught ; “* sea-weeds ” that contain enormous
stores of cellulose, chitine, and other substances that might be
used, but are not—and so on.
Here we are only concerned with the plaice. The quantities
that come into existence annually in the sea from the Solway
Firth down to the coasts of North Wales are probably illimit-
able—in the sense that fishing operations, as at present carried
on, do not appear to make any sensible difference in their
abundance. Of all the plaice eggs that are spawned in the Irish
Sea every year only a rather small percentage become trans-
formed larve. A certain combination of conditions, tempera-
ture of the sea, density, strength and direction of resultant
tidal streams and wind drifts, certain food organisms that
appear just at the right time and in the right quantity, intensity
of sunlight, ete.—probably all these and other conditions must
co-operate in a timed manner in order that a large proportion
of the fertilised plaice eggs produced during the spawning
period may develop into baby plaice. Then, just for the few
weeks that these larval plaice are living on the very shallow
sea bottom just outside tide marks there must be plenty of the
right kind of food organisms in the sand and in the water
immediately over the latter—it will be no use if this plentifulness
of food occurs a few weeks earlier or later than the very few
weeks when the little plaice come close to the shore. A certain
small proportion of the latter, therefore, are well fed and survive
for a couple of years to be caught by the inshore trawlers, who,
6
nevertheless, only catch a small fraction of the fish that are
there. Further on, after the plaice have become about three
years old, a small fraction of them migrate out into deeper
waters, beyond the territorial limits, and are caught by the
smacks and steam trawlers. Hitherto it is the fate of this
latter fraction of a per cent. of the whole plaice population,
annually coming into existence, that has been studied. Of the
fate of the plus 99 per cent. that perish before they are big
enough to be caught by a trawl-net we know hardly anything.
A very few, then, of the plaice that can be taken in a
shrimp-trawl migrate out to sea, become big, valuable fish,
spawn, and are sooner or later caught. This fraction consists
of individuals that have greater “ vitality,’ grow more rapidly,
are more “restless,” and are more precocious in their assump-
tion of sexual maturity than are the average fish. The mediocre
individuals—which constitute by far the greater number—are
less variable, and they tend to remain longer on the over-
crowded nursery grounds, where they develop and grow slowly.
How to assist them in obtaining better conditions of life may
well be the great task of fish culture of the future, and all
experimental and observational work and all practical trans-
plantation operations help to solve this problem. Then there
is the greater problem of the utilisation of surplus, ‘“‘ waste ”
production. The substance of the hundredweights of plaice
that die in the sea uselessly (in contrast with the ounces that
are caught usefully) is not lost, but appears later in the forms
of crabs, molluscs, worms, starfishes, sea-weeds, and a multitude
of other organisms that have—as yet—no commercial signifi-
cance for us: at the most we think about them as a possible
form, or source, of manure! Fishery work of the future will
probably be dominated by the impulse to utilise the waste
production of the shallow seas, just as that of the past has been
obsessed by the fear of depletion and has resulted in successive
crops of restrictions of very doubtful value, This idea of
ff
making use of surplus production seem to us to be the one
which must give the keynote to the scientific research of the
near future and reconcile the administrators to investigations
which, no doubt, seem abstruse and pedantic in the extreme.
Further Work on the Plaace.
Some other researches, which are not of a routine nature,
have been made, or are in progress, but are not published here.
A series of drift-bottle experiments and corresponding fish-
marking experiments were made by W. C. Smith in the study
of the Solway spawning grounds. These tend to show that the
area of the Irish Sea, north from Isle of Man and St. Bees’ Head,
is a self-contained one, so far as the plaice is concerned. Along
with this an account of the Cumberland sea-fisheries in 1919
has been prepared. Collections of small plaice were made on
the Manx and Cheshire foreshores by W. Birtwistle and W. C.
Smith, and the feeding of these has been studied by A. Scott,
who has also identified the food organisms found in a large
number of larval and post-larval plaice spawned and reared
at Port Erin: the results of this latter investigation are being
published elsewhere. Plankton is being collected from the
spawning and rearing ponds at Port Erin, and this is being
described by A. Scott, for comparison with collections being
made simultaneously in the adjacent sea. It is hoped that
some useful information as to the nutrition of larval plaice
may thus be obtained. Some much-needed experimental work
on conditions of metabolism of developing plaice eggs has also
been commenced by Professor Dakin, but this research is still
in the tentative stages. Finally, a study of morphological
variability in plaice is also bemg made.
The Biometric Investigation of the Herring.
In 1913 the Ministry of Agriculture and Fisheries requested
this Laboratory to take part in a general scheme of investigation
into the various races of herring which were assumed to inhabit
8
North European Seas. It was previously known that herrings
from the North Sea, Baltic, Norwegian coasts, etc., presented
various peculiarities—mainly in the proportions of the parts
of the body—and it was thought that these variations in form
were good evidence in favour of the idea that each great sea
area had a different ‘“‘ race” of herrings, and that there was
little or no inter-mixture between these various races. The
migrations and shoaling movements made by the fish were,
it was thought, all local ones. It was assumed that by making
large series of measurements certain bodily characters could
be found which would serve to distinguish between these
various races. The first series of measurements were made
by Mr. W. Riddell in 1913 and 1914, and the research was then
suspended until 1919, when it was resumed by Mr. W. Birtwistle
and Miss H. M. Lewis.
It was suspected that even in such a small area as the
Trish Sea there would be more than one race of herrings. It
is known, of course, that there are at least two such races :
one which shoals off the 8.W., 8. and 8.E. Coast of Isle of Man
sometime about May or June, and then spawns in August or
September, when the shoals disperse. Another school of
herrings shoals in Cardigan Bay sometime about October and
November, and then proceeds to spawn. In this case the
shoaling and spawning begin first at the southern extremity
of Cardigan Bay and then takes place a little later in the year
in Carnarvon Bay, and finally off the North Coast of Anglesey.
This is the usual progress of the fishing, and what we know
about it is derived from the catches made by the local boats,
for we have never been able to make big fishing experiments
ourselves. The herrings may, however, appear much earlier
in the spring, off the Manx coasts, than May, when the com-
mercial fishery usually begins, and it is quite possible that they
are there from the beginning of the year, but their quality is
so poor that it is not worth while catching them.
9
‘
Thus there appeared to be two “ races ” of herrings in the
Trish Sea—the Manx summer and the Welsh winter spawners.
But the conditions are not quite so simple as this. It has been
known for some years that herrings may be caught by means
of trawl-nets, and big catches were so made, before the war,
by steam vessels working in the North Channel (between
Scotland and Ireland) and in St. George’s Channel (off the
Smalls). Some of these fish were examined in 1913 and it
was found that they were different from those obtained from
the Isle of Man and the Welsh Bays. Further, in 1921 quite
unusual conditions were observed.
At various times in the past there have been commercial
fisheries for herrings off the coasts of Cheshire, Lancashire and
Cumberland, where the fish do not occur in the same regular
way that they are found off the Manx and Welsh coasts.
In 1894 they appeared in Liverpool Bay, and the Morecambe
vessels followed them, catching the fish with drift-nets in the
estuary of the Mersey itself and up the latter to near the
entrance to the Manchester Ship Canal. Quite big catches
were made for a time and then the herrings disappeared.
At various times in the past, even in the eighteenth century,
the herrimgs are recorded from the Lancashire and Cheshire
coasts, and there are many records of their occurrence in the
Minutes of Evidence of the various Fishery Commissions.
Long ago there used to be a fishery off the coast of Cumberland,
and the “ Parton Herrings,”’ caught a few miles north of
Whitehaven, had a great reputation and have left a kind of
legend in that part of the district. For many years, however,
there have been no herrings off the Cumberland, Lancashire
and Cheshire coasts, or, at least, not nearly enough to give rise
to a distinct fishery. Now and then, of course, a few fish may
be caught almost anywhere along these coasts, and the young
ones, of one year old or less, are always there.
At the end of 1921, however, Morecambe Bay was reported
10
to be “ full of herrings,’ and about the same time they were
being caught off the coast of Cumberland. Some small samples
were obtained, but not regularly, for there was no drift-net
fishery. (Quite big catches were, however, taken in the
“baulks ”’ at Heysham.) The fish were exceedingly lean and
were very poor eating. Most of them were spent though so
many were found to be “full” that it seems probable that
these fish were shoaling and spawning. Apparently they were
present all along the coast from the Solway down to Great,
Orme’s Head.
Thus we have to consider (1) the regular summer herrings
that spawn in the region between Ardglas, in Ireland, and the
Isle of Man, and (2) the equally regular winter spawning in
Cardigan and Carnarvon Bays : these two fisheries never appear
to fail. Then there are irregular fisheries which occur off the
Cumberland, Lancashire and Cheshire coasts after long intervals
of time.
When the biometric investigations were commenced it was
thought that each of these regular or irregular fisheries was
that for a distinct “race” of fish. In order to establish the
characters of these races a large number of fish had, presumably,
to be measured and studied. There is so much individual
variability between fish and fish that many hundreds would
have to be measured in order to get reliable average values
for each of the characters taken as diagnostic of the various
races. Also the measurements were rather delicate ones,
subject to some considerable, unavoidable errors; the fish
were not always in good condition when they were received ;
even the examination of so small a sample as 50 was quite a
long job; different measurers did not always get precisely
the same results; Wwe were never quite sure what were the
best “‘ characters’ to measure—in short, the methods were
not perfectly satisfactory ones and it was thought
desirable to suspend the routine collection of data for a
et
while and see what was to be made out of those already
accumulated.
Believing that there were only the two main “ races ”—
the Manx and Welsh ones—we thought the best method was
to spread the collection of measurements over several years
and to “lump ” together all the samples obtained from Isle of
‘
Man, irrespective of the month or year of collection. So also
with the Welsh fish. In that way we hoped to get such big
series of data that the averages, and other statistical functions
deducible therefrom, would be fairly representative ones.
Now this method may be quite wrong.
Even with quite small samples taken in the same region,
and after intervals of some weeks, there may be quite noticeable
differences: differences as big as those obtained when we
contrast the fish taken from Isle of Man with those taken from
the Welsh coasts. This may, conceivably, be the case even
if we hold that there are only the two main races. It may be
¢
that in taking the sample this week we have “ accidentally ”
included more of the herrings that vary from the average in one
direction while, in the next small sample, we may have included
more of the herrings that vary from the average in the other
direction. If this is so there is a test, based by Professor Karl
Pearson on the statistical theory of random sampling, which
can be applied.
But it is also possible, and some results of general biology
make it quite likely, that there is another explanation. It may
be that, instead of two main “ races ”’ there are really a number
ee
of “ sub-races,” or “ genotypes,” that is, strains of herrings,
that are really permanent, or the same from generation to
generation, except in so far as they may vary by inter-mixture
with each other. This inter-mixture may, however, be regarded
as rather improbable because of the tendency of the herrings
to remain together as lonely aggregated schools. There are,
then, a number of strains, or genotypes, of Irish Sea herrings
12
differing from each other in those shapes, or proportional
lengths of parts of the body which we call morphological
characters, and those differences which we can observe in
studying samples obtained month by month from the same
fishery region may be due to the successive appearance of
the various genotypes, or to the predominance of one or more
of them in the samples. Further, the various genotypes may
respond differently to the nature of the environment, the
temperature and salinity of the water, or the reaction or some
other physical condition. In the course of the Manx summer
fishing, for instance, these physical conditions change markedly,
and so there may be successive immigrations of different
herrings—something like this is really what the fishermen appear
to think is the actual case. If so, then, it will be wrong in
principle to adopt a method of “lumping” together data
obtained from the same region in order merely to get the big
samples, which appear to be necessary from the statistical
point of view.
It is with these considerations in mind that a critical study
of the methods and data of the herring race investigation has
been attempted by Mr. Birtwistle and Miss Lewis.
Shellfish Investigations.
Two troublesome questions arose in the course of the
administrative work of the Committee: (1) the alleged over-
crowding of some of the cockle beds in the neighbourhood of
the Dee, and (2) the pollution of the mussel beds in the estuary
of the Ribble. ‘The former difficulty originated im complaints
made by some fishermen that the cockles on certain beds were
so small that most of them passed through the legal gauge.
This was probably the case, but the matter was not to be
remedied by reducing the legal size and so enabling a few men
to glut their customers with small cockles fetching a much
smaller price. In such circumstances the remedy must lie in
13
transplantation. The beds were examined and counts made of
the numbers of cockles present in a square foot of sand on various
parts, but the investigation was not pressed since it had little
interest except where associated with some other shellfish
research, which we have not yet been able to start. It has
now been shown by the past work of the Committee that
conditions of local overcrowding and stunting of growth, both
with regard to cockles and mussels, can easily and profitably
be remedied by transplantation. The difficulties are adminis-
trative ones and are only to be removed by a rational system
of control over the foreshore fisheries.
The Ribble Mussel Fisheries.
In 1921 the mussels taken from the Ribble Estuary again
came under suspicion and several inspections were made by
Messrs. Scott and Birtwistle, with the cordial assistance of the
Harbour Authority. I saw this district in 1913, when there
was also suspicion that mussels growing there were communi-
cating typhoid fever. Very marked changes have occurred
and these are due to the extension seaward of the training walls
built in order to establish the new channel leading up to the
Port of Preston. Charts marked then and in 1921 show these
changes very clearly, and the altered conditions must be taken
into account. The fact is that an almost continual revision
of the charts representing the conditions of the mussel and
other shellfish beds, channels and sewer outfalls is quite
necessary in order that this question of sewage contamination
may be studied in a really satisfactory manner. Every case
that arises demands renewed local survey.
There are two implicated regions in the present case :
(1) the mussel beds on the foreshore, adjacent to the St.
Annes-Lytham shore, and (2) the mussels growing on the
training walls, much further away from the primary sources
of pollution. The precise locality under (1) in question in
14
1921 was that known as “ Church Scar,” and this is subject
to recent and significant sewage pollution. The adjacent shore
is the locus of a good, residential population, and it is a well-
known holiday resort, so that the contamination of the sea
in its vicinity cannot be said to be free from danger. It is a
place where people may go to recuperate after illness, and so
there is always the chance that convalescent typhoid patients,
who are still in the infective stage, may be temporarily resident
there. The distance between the mussel beds and the sewer
outfalls is short, and so quite a small period of time may elapse
between the discharge of dejecta into privies ashore and the
fouling of the mussels with the resultant sewage, which is
quite untreated. There has actually been a barge (with a
privy on board) moored on the Scar and inhabited by workmen,
but we are inclined to regard this contributory source of pollu-
tion as less objectionable than that resulting from the much
better-off population living in the St. Annes-Lytham district.
The case is rather different with regard to the pollution
of the channel adjacent to the training walls. Much of this
must have its origin at Preston and the distance is therefore
considerable and the pollution remote in pomt of time.
Bacteriologically there is little difference between the two
regions (1) and (2), but the strong impression made on Messrs.
Scott and Birtwistle in 1921 and on myself in 1913 was that the
bacteriological evidence might safely be neglected so far as
the training wall mussels were concerned. Thus we disregard
the bacteriological evidence, though the latter shows that the
contamination both at Church Scar and on the training walls
is gross in its degree. It is fair to say that the conditions on
Church Scar are such that closure is to be urged, but this
conclusion we are reluctant to make in the case of the other
locality.
Something must therefore be said as to the general question
of shellfish pollution by way of justifymg these findings and
15
also because this matter looks like again becoming one of
public importance.
Enteric Fever and its Incidence.
It is instructive to notice the very remarkable way in which
the mortality from enteric fever has diminished during the
period of modern public health administration. The following
figures have been extracted from the Report of the Registrar-
General for 1919, and the decrease is most obvious :—
Death Rate, per Mullion Persons living in England and Wales,
from Enteric Fever during the last 80 years.
1838-1842 ... ee 058 1891-1895 ... sev DTA
1847-1850 ... we ol246 SIO L900 an, a lno
1851-1855 ... noon heb 1901-1905 ... ceey ) tS
1856-1860 ... bout Oe 1906-1910 ... dais 70
1861-1865 ... Shed asp re 1911*1915 ... uae 47
1866-1870 ... jth 2O00) 1916 as ae 30
1871-1875 ... yee ole 1917 fe wale 28
1876-1880 ... arene AUT 1918 as as 26
1881-1885 ... sap, oil) GS) es ass 16
1886-1890 ... 179
It is to be noted that the statistics from 1838 to 1870
include enteric fever, typhus fever and pyrexia, these diseases
not being distinguished in the above data for the period in
question. There can be little doubt that the contribution
made by the two latter causes was considerable during the
first half of the nineteenth century. The conditions due to
the rapid development of the modern factory system, the
overcrowding and insanitary housing of that period, unemploy-
ment and general malnutrition among much of the artisan
and labouring classes during the “hungry forties ’—these
were, no doubt, responsible for the “ destitution disease,’ which
we now know typhus to be. About 1870, however, enteric
fever became distinguished, and it alone appears in the table
for the years subsequent to that date. During the latter half
of the nineteenth century typhus fever practically disappeared
16
from England—the result of better housing and nutrition,
and plain, commonsense methods of sanitation.
But even when we take account of this qualification of the .
meaning of the table it is plain that the mortality from enteric
fever has steadily diminished throughout the whole period,
and this is so even during the war years 1914-1918 (for which
years the death rate is calculated only for the civilian popula-
tion). One might, at first sight, have expected some relaxation
of public health administration during those years of strain,
but this has not been the case—the rate of decrease is even
creater than it was in the preceding decade. The entire record
is a remarkable and very creditable one, and it ought to lead
to a renewed appreciation of the medical service as it is
organised in this country. It does not, at first, occur to one
to reflect that this is the only profession which, by perfecting
its work, tends always to render itself unnecessary !
It would be worth while, if there were the opportunity,
to examine into the measures by which this notable reduction
in the mortality from typhoid has been brought about. It is
probable that no one line of public health work is to be singled
out—for instance, prophylactic treatment only came into
general use during the war period and was applicable only
in the war services. What we have to thank for the effect
noted has been the consistently maintained and always
improved public health administration and a general, all-round
effort to do all that is possible to minimise the chance that
any person whatever in the population might contract epidemic
disease, because with modern means of intercommunication
the risk of infection has always tended to become greater, and
class-distinctions tend to have no significance in this connection
—it is all the same to the public health administrator what is
the social standing of the patient: the labourer incubating
for typhoid and using a privy on a barge moored on Church
Scar has just the same “ epidemiological value,’ neither more
17
nor less, as has a Manchester millowner residing at St. Annes,
if the latter also harbours Bacillus typhosus. This attitude
has its significance: any person who is suffering from typhoid
fever is a focus of infection ; the service is a public one, and its
result has been the preservation of the health of the individual.
And so, because of the existence of medical research, no one
cause of dissemination of enteric has, for any great length of
time, been over-estimated in value by the public health
administration ; on the other hand fishery authorities have
rather tended to become obsessed with the idea that mussels
are the way in which typhoid is carried. It has been said that
there still remains a persistent residue of the disease and that the
cause is polluted shellfish, but in view of the now generally
recognised fact that apparently healthy persons may be
“typhoid carriers ” this view cannot be maintained.
The evidence that Enteric Fever is conveyed by Shellfish.
Without doubt the consumption of sewage-infected oysters,
mussels and cockles 7s a cause of enteric fever, but a candid
survey of all the available evidence does not convince one
that this is even a prominent cause. It must be remembered
that the role of shellfish in conveying the infection has only
been attentively studied since 1894, when the late Dr. H. T.
‘
Bulstrode made his well-known investigation into “oyster cul-
ture in relation to disease.” Further, administrative measures
designed to prevent communication of typhoid by this means
cannot have been effectively applied until the first few years
of the present century, yet a glance at the table on p. 15 will
show that an enormous decrease in the mortality from the
disease characterised the last decades of the 18’s. For this
decrease we must therefore look to other action than that
taken with respect to polluted shellfish, and the same kinds of
action have doubtless continued to be taken,and with the same
success, during the last dozen years or more. The statistics
B
18
show that the residue of enteric is certainly not a persistent
one, and one need not hesitate to conclude that some of it, at
all events, is due to the existence of “carriers,” imsanitary
dwellings, slums, locally defective drainage, open middens,
ashpits, flies, etc. It is probable that far more stringent
sanitation in the overcrowded quarter of big towns will be
necessary to reduce the mortality to vanishing point, than has
been necessary to arrive at the present rate. The residue is
small, but the risk of any one person dying from enteric is still
appreciable, while the risk of illness is, of course, much greater ;
it is no consolation to the typhoid patient to reflect that his
is only one of the dozen or two cases per million !
There is, of course, satisfactory evidence that typhoid
fever is conveyed by means of polluted shellfish, yet it is very
surprising to find that such satisfactory evidence is rather
exceptional. If it were not for the well-known cases of
epidemic illness following the two famous mayoral banquets
at Winchester and Southampton (the cases investigated by
Bulstrode) such evidence as is often adduced at the present
time would lose a great deal of its force. These two classic
investigations have, in fact, established a tradition which
subsequent work can hardly be said to have maintained. It
will be useful to quote some instances of the kind of evidence
that has been regarded as proving the connection of typhoid
fever and shellfish consumption :—
(1) A ate steamed mussels on September Ist and fre-
quently from then to November 29th. Then he
ate a raw mussel and said to his wife that it was
not good. He became ill on December 4th. His
blood reacted positively on December 27th. He
died on January 12th.
(2) B ate cooked mussels on December 17th and he was
ill seven days later. His blood gave a positive
reaction on December 29th. He died on January 3rd.
19
He had influenza prior to November 24th. All his
family ate cooked mussels on December 17th, but
he was the only one who became ill.
(3) C ate raw and cooked mussels at the beginning of
December. Other members of his household ate
cooked, but not raw mussels. C was ill on Dec. 12th,
and on December 31st his blood gave a positive
reaction. He died on January 27th.
(4) D ate steamed mussels and a plate of oysters at a shop
on December 21st. She was ill on January 3rd, and
her blood gave a positive reaction on January 10th.
She died on January 16th. Her three companions
also had mussels at the same time, but they had
had enteric fever about two years previously and
they did not become ill.
(5) E ate cooked mussels on December 21st and was ill
on December 28th. His blood reacted positively,
and he died on January 24th. A friend who was
with him also ate mussels, but did not become ill.
All the above are actual records and they may be regarded
as quite typical of the kind of evidence that has been taken
as establishing the connection between mussels and disease.
“From a review of all these cases there appears to be little
doubt but that the association between enteric fever and
mussel consumption is something more than mere coincidence.”
That was the opinion of most Medical Officers of Health, and
may be so still, but nevertheless there have been other ways
of looking at the facts.
In 1910 there was an outbreak of enteric fever in the
London districts of Bethnal Green, Stepney and Poplar.
There are various criteria by means of which outbreaks due to
personal infection, polluted water or milk can be recognised,
and these criteria were applied by the London Health Officezs
in investigating the origin of these outbreaks. A process of
20
‘hypothetical deduction ” applied during the enquiry showed
that the epidemic was an “explosive one” (that is, a great
number of cases occurred at the same time and not one after
the other); therefore it was not due to personal infection
(that is, the communication, by direct contact, from person
to person). Further enquiry gave no reasons for supposing
that contaminated water or milk were causes (in which cireum-
stances the outbreak would have been “ explosive ”’). Two
articles of food, however, were consumed by a “ considerable
proportion ” of the patients durmg the month preceding the
onset of illmess—these were mussels and fried fish—but further
enquiry showed that the mussels might be disregarded. There
remained, then, the possibility that fried fish were the means
by which the disease had been communicated.
The fish implicated were plaice which had been caught
on the “ nursery grounds” of the North Sea, and, as a rule,
they were poor quality fish. Plaice are very usually gutted,
but it was suggested that, in this case, the process of gutting
had been imperfect. These North Sea grounds are, it might
be thought, very far away from sources of sewage pollution,
yet it was concluded that the possibility of contamination
“was not so remote as might at first be supposed.” Further,
the fish were fried, and this process may be imagined effectively
to sterilise small plaice ; nevertheless the contaminating germs
assumed to be present in the tissues of the fish were also
assumed to have survived the ordeal of boiling oil.
Such enquiries as this, and the other ones quoted above,
are usually very well done. There is a regular technique, and
the investigators employed are well-trained men who are
thoroughly conscious of the great responsibility of their work
and who therefore do that work consistently well. Yet here
we have, on the one hand, enteric fever occurring in a mussel-
eating population and a causal association established between
the mussels and the disease, and, on the other, a group of cases
21
occurring in a population consuming both mussels and fried
fish, with the result that a causal association is set up between
the fried fish and the disease. As a matter of fact the first
population—that is, the one in which mussels were regarded
as the cause of the disease—was also a fried-fish consuming one.
We can hardly doubt that much the same conditions obtained
in both populations and that there were various ways in
which enteric fever might have been communicated, but that,
in each case, the Health Officers took one particular aspect
of the whole problem. In the first group they were influenced
by the Bulstrode tradition, but in the other a spirit of
scepticism with regard to accepted methods was allowed to
gain force.
It is quite fair to say that the evidence which implicates
6
mussels is ‘‘ coincidence.” A man eats mussels and, a week
to a fortnight later, he shows that he is suffering from enteric
fever. The typhoid germs require a week to a fortnight to
‘incubate ”’ in the man’s body and cause the symptoms of the
disease. That may be ‘‘ mere coincidence,” but all scientific
proofs are based on just such associations, coincidences in regard
to events that happen simultaneously or after a certain period
of time. The probability of a causal connection between two
such events is small, and it has to be strengthened by the
establishment of a series of other coincidences such as, for
instance, those that were observable in the cases of the out-
breaks following the mayoral banquets at Winchester and
Southampton. The strength of the evidence in the latter
cases was due to the number of coincidences, and its weakness,
in the cases A to H, on pp. 18-19, is due to their paucity.
A certain shop sells mussels which are, presumably, all taken
from the same contaminated shellfish bed, and a man buys
and eats these mussels and then takes enteric fever a week
to a fortnight later. But we ought not to overlook the other
coincidences, which seem to me to have just the same value
22
as scientific evidence : a great many other people buy and eat
just the same mussels, but they do not take enteric fever.
It is quite easy to make an explanation of this apparent
contradiction. Probably infection by organisms setting up
typhoid, and other infectious and contagious diseases, is far
more common than used to be imagined. Many of these
organisms are ubiquitous, and modern conditions of life must,
in many cases, greatly increase the chances of their distribution.
In no case do men and women yield easily to infection for the
defences set up by the normal healthy body are fairly strong.
The infection may not “take” at all (and pathologists must
encounter such failures, even in experimental work), and if
it does “take,” it may successfully be resisted. There are
many ways by which Bacillus typhosus may be distributed—
by contaminated water, milk, vegetables and fruit, flies, carriers,
shellfish, personal infection, and perhaps also fried plaice.
Certainly some of these may be ruled out in many cases—water
and milk in modern conditions of public health administration,
for instances, but, as a rule, there must generally be more than
one means. Further, it is probable that there are conditions
which are necessary in order that the imfection may take.
It is probable that the bodily “soil”? must be such that the
pathogenic micro-organisms may grow: there may have to be
symbiosis with some other organism; or a condition of
‘‘ rundownness ”’ due to malnutrition, overcrowding, insufficient
warmth or clothing, etc. ; or some set of environmental con-
ditions which we do not understand. The progress of epidemics
does suggest this: that a number of conditions must coincide
and co-operate in order that the pathogenic organism (which
is thus only the immediate “ cause ’’) may be enabled to operate
upon the bodily “soil.” Thus public health practice, while
it may not neglect these exciting, or immediate causes, may
neither afford to neglect the essential co-operating ones. In
short, the role of shellfish as a contributory cause of disease
23
cannot be overlooked, but it can greatly be exaggerated. It
is probable that entire exclusion of mussels from the public
markets would not greatly reduce the incidence of enteric fever,
while it is also possible that a very highly perfected system
of public sanitation, in the widest sense, might reduce typhoid
to the status of typhus without interfering greatly with the
use of shellfish as human food.
The Administrative Procedure with regard to Contamined
Shellfish.
The above discussion will throw some light on the utility
of the present administrative methods ; these date back only
to 1915, when the Local Government Board made the “‘ Shellfish
Regulations,’ under which action with regard to polluted
mussels is now taken. Prior to 1915 little or nothing was done.
Various Health Authorities were able to exclude mussels from
the public markets under their control, and, apparently, they
based their action on the inspectorial work done by their own
officials (that is, they moved on the kind of evidence furnished
by the quoted cases on pp. 18-19), or they took action on
inspections made, and bacteriological analyses procured by
the Fishmongers’ Company of London. Obviously they could
only exclude mussels from the public markets, but could not,
in general, prevent the sale of the shellfish by hawkers, or in
retail fish shops. Attention was drawn to the matter, but
it is not certain that much more than that happened. There
was no closure of the polluted shellfish beds prior to 1915
because no public authority possessed this power.
The “ Shellfish Regulations ” conferred this power on the
Local Health Authorities, and the Central Authority is now the
Ministry of Health. The procedure is interesting: if the
local Medical Officer of Health “is in possession of information
that any person is suffering, or recently has suffered, from
infectious or other disease attributable to shellfish, or that
24
the consumption of shellfish within the district is likely to cause
danger to public health, he shall take such steps, etc.” The
steps are the holding of a local enquiry at which the fishermen
are called upon to show cause why the shellfish beds suspected
should not be closed to ordinary fishing. This procedure, which
apparently bears rather hardly on the fishermen, does not do
so in reality, for its result must usually be to put the local
fishery administration on their side: the latter does not appear
to have any definite locus standi in the matter in the course
of the enquiry. Here, too, it is quite relevant to ask for the
definite results of such enquiries and closures that have taken
place, for the making of an order closing a certain mussel bed
is not at all the same thing as the prevention of taking mussels
from that bed. Have the ‘Shellfish Regulations” really
prevented the marketing of polluted mussels? We are
enquiring into the causes of the decrease in enteric fever during
recent years and so the question is a relevant one.
The important thing in the ** Shellfish Regulations ” is the
phrase attributable to shellfish. What evidence satisfies the
Medical Officer of Health that any particular case of typhoid
fever has been caused by eating, say, mussels. Study of the
cases quoted above will show, I think, that there is no satis-
factory legal evidence at all. A man takes the disease, and the
investigators discover that he has, during the two weeks
previously, eaten shellfish, bought at a particular shop or stall
or barrow in the streets. There is no possibility of proving
that these particular shellfish were competent to cause infection,
because it is only sometime after they have disappeared that
their association with a case of disease was suspected. Enquiry,
however, shows that shellfish of the same origin are still being
sold, and these are analysed and are found to contain evidence of
sewage pollution. Thus the outbreak of disease is “ attributed ”’
to them. Now the association thus set up is so loose and
unsatisfactory that we are impelled also to consider the fact
25
that just the same shellfish were eaten by a number of people
without detriment, and this surely robs the original identification
of the shellfish with the cause of the disease of much of its
force. The proof cannot be regarded as satisfactory, and |
think the ‘attribution’ of disease-conveying properties to
mussels, in some such case, ought to be challenged in the
Courts in order that some legal decision as to what constitutes
the proof should be obtained.
The Validity of the Bacteriological Evidence.
Nor can the results of a bacteriological analysis find legal
proof that the ilmess was the result of eating mussels that
contained typhoid bacilli, because when the illness is being
investigated its presumed material cause no longer exists.
It must be remembered that it is a very uncommon thing
indeed to find Bacillus typhosus in mussels taken from the
foreshore. I have found it myself, on one occasion, but even
then the identity of the organism was not beyond doubt.*
What the bacteriologist does look for, and usually find, is the
presence of what he calls Bacillus coli. This may be backed
up by finding that various other organisms of the same category,
Streptococci and B. enteritidis sporogenes, are also present.
The occurrence of these organisms is held to prove, and usually
does prove, that the shellfish in which they were contained
have been living in sea-water which contains sewage organisms
proceeding, via sewer outfalls and drains, from human dejecta.
None of these organisms, of themselves, convey enteric fever,
and all that is shown by the results of the analysis is that the
mussels were living in such conditions that they would have
taken up (and retained for a short time) typhoid bacilli had those
bacilli been present in the sea-water in which they were living.
The proof, from bacteriological analysis, is really this: had a
* The biological characters were those of B. typhosus, but the agglutina-
tion test was not a very stringent one and the further proofs were not
attempted.
26
person suffering from, or convalescent from, or a carrier of
typhoid fever been living in the area drained by the sewer
discharging near the mussel bed, then the shellfish maght have
become infected and persons eating those shellfish might have
contracted typhoid fever.
But the bacteriological evidence is really weaker than has
just been indicated, and I may quote Bulstrode with advantage :
The Report on “Shellfish other than Oysters,’ of 1909-10,
says: ‘‘It was found during the enquiry relative to oysters
that bacteriological investigations yielded conflicting results,
and it cannot be said that bacteriologists are in agreement as
to the standard to be adopted, and this seems to be the case
whether regard be had to the total number of organisms
present, the percentage proportion of certain organisms or the
mere presence of certain organisms. It has also to be added
that there are at present no tests which will serve to distinguish
sewage micro-organisms of human origin from those of animal
origin, and even if it were practicable or desirable to distinguish
between the two it would be difficult to fix reliable standards
when dealing with estuarial waters draining a whole catchment
area, much of which might be devoted to grazing purposes.
“Tt is necessary, too, to point out that the standards
adopted by some bacteriologists would not improbably serve
to condemn every shellfish bed round the littoral. Possibly
the time may come when a standard of this nature may be
regarded as desirable, but, in the meantime, a useful provisional
standard is one based upon topographical and epidemiological
evidence.”
The above passage was written over a dozen years ago,
but the matter remains precisely where it was then. The
conditions at present are these :—
There is no generally recognised routine method of identi-
fying and enumerating the ‘
shellfish.
‘colon bacilli”? found in
27
There are no certain means of distinguishing between
bP)
“colon bacilli’? of human and lower animal origin,
when such are found in shellfish.
All mussels are polluted by ‘‘ sewage bacilli’ to some
degree.
There is no standard above which one is justified in
regarding the degree of pollution as noxious.
In spite of the importance of the subject, the amount of
administrative attention it has received and its susceptibility
to scientific investigation this is still the case, as it was in
1910, when Bulstrode completed his second report.
So I do not recommend any action, on the part of the
Committee, with regard to the mussel beds on the Ribble
Channel training walls. The matter has been discussed at
some length because it may again become very troublesome
and analogous cases may have to be investigated. In such
cases as that of Church Scar, where the pollution is gross,
immediate, and patent, action may be taken, though, of course,
it cannot be taken by the Fisheries Committee. In most
other cases, however, the best policy may be for the Committee
to oppose any further orders under the Shellfish Regulations
should these be initiated in their District, unless the order
carries with it an undertaking to provide facilities for cleansing
the suspected mussels. If bacteriological evidence is adduced
this should be controverted on the ground that there has been
abundant time for investigation—which has not been made—
and that without this investigation the methods of analysis
at present practised are inadequate. A legal decision as to
what is to be understood by the expression “ attributable ”
in the Regulations ought to be obtained.
It has been shown by Professor Klein in 1904, by experi-
ments made by this Committee in 1906-12, and by the results
obtained at Conway by the Ministry of Agriculture and
28
Fisheries, since 1914, that highly-polluted mussels can be
cleansed. Provision for such cleansing process ought, then,
to go along with any order made under the Regulations. By
itself an order is merely a restriction leading to a legal offence—
if it is enforced. If it is to be enforced then it is fair to the
fishermen to insist that the evidence on which the order is to
be made should have the same weight as that which would be
submitted to a magistrate against a delinquent who is to be
prosecuted under the order.
OTHER INVESTIGATIONS IN PROGRESS.
Hydrographic Research.
The Liverpool] Laboratory has now arranged for the
monthly collection of sea-water samples and the observation
of sea-temperatures in the Irish Sea. This is part of the scheme
of “ directed research ”? submitted by the Ministry of Agricul-
ture and Fisheries. Three cross-channel steamship routes will
be sampled: Fishguard to Rosslare; Holyhead to Dublin,
and Liverpool to Isle of Man. It is expected that the work
will begin in May.
The Life-history of the Cod.
This is also part of the scheme of directed research.
Investigations have been going on since October. There are
two main cod fisheries which go on during the winter and
spring—oft the Cumberland coast and round Isle of Man ; the
fish, of course, occurs nearly everywhere, but these are the main
fisheries. The Whitehaven fishery this year was poor, but the
Manx one was very good though the difficulties of transport
were so formidable that the season has been an unprofitable
one. The fishery, during the spring, both at Whitehaven and
at Isle of Man is one for cod that come inshore in order to
spawn, and by Easter the Manx fish had nearly all spawned.
A very good series of measurements has been obtaimed by
29
Mr. W. C. Smith, and scales have been preserved for future
study. A series of chemical analyses of the flesh and liver
of Port Erin cod has also been made on samples obtained every
few weeks, and it is hoped that these will fit into a bigger
scheme of investigation of the seasonal changes in the meta-
bolism of marine animals and plants in the Irish Sea area.
The changes in general “‘ condition’ of the fish durmg the
season have also been observed, and other lines of investigation
will, no doubt, present themselves later on.
The Chemical Composition of the Mussel.
A preliminary study of the chemical composition of the
common mussel has been undertaken by Mr. Daniel, and the
results of this are published in the tables given on pp. 217-221.
As this investigation has proceeded many interesting questions
have been suggested—the nature of the substance which is
called “‘ glycogen,” for instance. It cannot be doubted that
this is not the same, chemically, as the glycogen of the warm-
blooded animal, and difficulties and anomalies encountered in
the course of the work suggest that an exhaustive research
on the nature of the carbohydrates found in molluscs is very
desirable and may be of economic value in view of the further
utilisation, in some form or another, of the organic material
found in mussels. The use of the molluscs as human food,
in the fresh condition, has been decreasmg for years past
because of the somewhat bad reputation they have now
received from the Public Health Authorities, and, as things
are, their total exclusion from the food markets seem only
to be a matter of time. Year by year, for instance, an increas-
ing fraction of the great Morecambe supply goes to the Kast
Coast as bait for the liners, and until a good method of cleansing
them from sewage pollution can be generally applied this
tendency will continue. We have to reckon, then, on finding
some new use for the huge supply of material which the
30
Lancashire mussel beds can provide without diminution, and
some means of converting the flesh of mussels into a food
commodity ought not to be impracticable. The so-called
glycogen, for instance, may possibly be extracted by some
fairly simple, large scale process and applied to some useful
purpose: so much Mr. Daniels’ results seem to indicate.
There are, of course, other purely chemical or bio-chemical
problems that have arisen in the course of this research, but
these must be left for more detailed work. In the meantime,
and as a study preliminary to that more detailed work, this
research on the seasonal variations in rough chemical com-
position is of indispensable value.
A good deal of histological work, dealing with the mode
of distribution of fat and carbohydrate in the various tissues
of the mussel, has also been done by Mr. Daniel. Here, again,
all the methods given in the text-books and memoirs have had
to be tried and varied to suit the particular nature of the
tissue substances. Evidently we cannot speak simply about
“fat? and ‘“‘ carbohydrate ” in “‘ molluscs ” and depend upon
the application of any general method of fixation and tissue-
staining, for it seems probable that the precise chemical nature
of these substances may vary from group to group of mollusca
and even in the different species. Only in this way can the
anomalous results obtained be explained. A great deal of
preliminary work has, therefore, had to be done, and the results
of this, and further research on the histology and morphology
of the mussel, must fall to be recorded in later reports.
Other lines of work have been touched, but it is, perhaps,
unnecessary to make reference to these in the meantime.
The past two years have been a period of considerable difficulty ,
but it is to be hoped that they have also been preliminary to
the complete re-development of the scientific work of both
the Liverpool and Piel Fishery Laboratories. We have many
pieces of research in contemplation—some of them having a
31
far from indirect economic interest—and it is expected that the
near future may give us the opportunities for the full prosecu-
tion of these researches. We acknowledge here, with much
appreciation, the assistance given by the Development Commis-
sioners and the Ministry of Agriculture and Fisheries, and look
forward, with confidence, to the continued interest of these
departments in the marine biological and fishery work, which
has so long been carried on in the Irish Sea.
JAS. JOHNSTONE.
DEPARTMENT OF OCEANOGRAPHY,
University, LivERPOOL,
April, 1922.
32
CLASSES AND OTHER WORK AT PIEL.
By A. Scott.
Classes at Piel.
Two classes in Marine Biology and Navigation for fishermen
were held in the spring of 1921. The first one met during the
period 7th to 18th March, and was attended by fourteen men.
The second was held between 18th and 29th April, and was
attended by thirteen men.
The following are the names of the fishermen who attended
these classes :—
7th to 18th March.—W. Rimmer, Blackpool; Victor
Houghton, F. Woodhouse, H. Woodhouse, R. Woodhouse,
R. Gardner, J. Parkinson, Morecambe; Robert Burrow,
Bolton-le-Sands ; Robert Burrow, Isaac Burrow, F. Dickinson,
Grange-over-Sands ; Thos. Wilkinson, Baicliff; Thos. Butler,
8. Benson, Flookburgh.
18th to 29th April— J. H. Atkinson, Richard Wright (1),
Richard Wright (2), Fleetwood; Fred Taylor, J. Baines,
Bolton-le-Sands ; J. Dickinson, Silverdale; Frank Dickinson,
Allithwaite; P. Benson, M. Cowperthwaite, Flookburgh ;
H. Bayliff, W. Benson, Baicliff; Thos. Butler, Aldingham ;
W. J. Edmondson, Rampside.
Mr. R. J. Daniel, of the Oceanography Department,
University, Liverpool, had charge of the whole of the teaching
work.
In the interval between the fishermen’s classes, Mr. R. H.
Wardle, M.Sec., of the Zoology Department, Manchester
University, brought a party of senior zoology students to
examine the fauna and flora of the shore in the vicinity of the
Laboratory. The following is the report supplied by Mr.
Wardle at the conclusion of the visit. It gives an account of
the work done and the facilities provided for workers.
33
Mr. Owen Hunt, one of the senior students, was unable
to join Mr. Wardle’s party, but came later, 2nd July, and spent
a week investigating the shallow-water fauna.
Report upon Visit of Zoological Party to the Biological Station,
Piel, Barrow-in-Furness, during April, 1921.
The party under my charge consisted of the following
eight students :—Misses MacGill, Allen, Comstive, Bishop,
Dutton, Wainwright, Mr. Hopwood and Mr. Lean.
The party left Manchester on Friday, April 8th, by the
10.25 train to Fleetwood, were met at Wyre Dock Station by a
member of the crew of the “ James Fletcher’ and conducted
to the vessel. Upon this steam trawler an exceptionally
interesting and instructive nine hours were spent as the guests
of Dr. J. T. Jenkins, Superintendent to the Lancashire and
Western Fisheries Committee. At a point 14 m. W. by N.
from the Morecambe Bay Lightship an otter trawl was shot,
was dragged for seven miles in a W. by N. direction, and was
hauled at 5.30 p.m. A record was obtained of the 311 edible
fishes caught, and the Invertebrate contents of the trawl] were
set aside for further examination ashore. The party were
landed at the jetty, Piel Harbour, at 9 p.m.
Saturday was spent in examining the Invertebrate material
and the tow-nettings obtained the day before.
Monday.—A collecting expedition to Foulney Island was
organised, under the guidance of Mr. Andrew Scott, in the
morning. The material thus obtained was examined during
the afternoon in the laboratory ; living plankton, obtained by
tow-netting from the end of the jetty, was also available for
examination.
Tuesday : a hot, calm day.—The party, accompanied by
Mr. Scott, boarded the police cutter at 10 a.m. and spent most
of the morning and afternoon tow-netting in the Walney
Channel, in charge of the Committee’s Officer, Mr. J. Wright.
Cc
34
A beam trawl was shot and dragged for two hours, and the
resulting catch examined and sorted out for examination ashore.
Wednesday: cold and wet.—The morning was spent
collecting along the foreshore west of the harbour, but little
was obtained.
Thursday.—The party went out in the morning under
Mr. Scott and obtained a supply of Arenicola ; the rest of the
day was spent in examination and dissection of this material,
and in examination of segmenting ova of the plaice.
Friday.—In view of the threatened railway strike, |
decided to bring the party back to Manchester, and wired
Dr. Jenkins to that effect. Otherwise, the party would have
stayed until Monday, the 18th, and returned to Fleetwood
on the “ James Fletcher.” During the morning a very interest-
ing lantern lecture upon the Fisheries of the Morecambe Bay
area was given by Mr. Scott. The party left Piel on the
1.13 train.
General Remarks.
In spite of the unfortunate curtailment of our visit, a
surprising amount of work was carried out, and the visit was
in every way a success. The muddy and shingly foreshore
is far more plentiful in variety of animal life than would appear
from a cursory examination, and to the assiduous and
experienced collector is not greatly inferior to a rocky coast
such as obtains at Port Erin.
Any inferiority of littoral fauna was, however, compensated
for by the facilities afforded by the Fisheries Committee’s
steamer.
The laboratory facilities are equal to those prevailing in
the University laboratory. There is bench accommodation
for sixteen students, there are fifteen good Leitz microscopes
and a Zeiss binocular, there is a plentiful supply of glassware,
dishes, instruments, reagents, etc. In the adjoining fish
35
hatchery is a series of tanks and bell jars into which living
material may be placed and kept under observation. We
were thus able to observe fully-expanded specimens of
Alcyonium, Actinoloba, various Hydroids, Nudibranchs, etc.
Attached to the laboratory is an excellent library, and in the
laboratory itself is a very complete collection of preserved
specimens of Irish Sea fauna, which is available for teaching
purposes.
The success of the visit was undoubtedly very largely due
to the energy and forethought shown by Dr. Jenkins and to
the assistance of Mr. Andrew Scott, who sacrificed much time
and trouble in conducting the party on collecting expeditions
and in identifymg obscure or out of the way species.
R. A. WARDLE.
Dr. Stuart Thomson, also of the Zoological Department,
Manchester University, who had carried on an evening class
in Marine Biology in the winter, which was attended by
members of the Manchester Microscopical Society, brought a
party of thirteen members. This party was at Piel from the
14th to the 21st May. The course consisted of lectures and
demonstrations, examination of living material, shore collecting
and photographing.
A class in Marine Biology and Navigation for school
teachers was conducted by Professor Johnstone and Mr. Daniel
from August Ist to 12th, and was attended by the following
eight schoolmasters :—A. KH. Morley, Scarborough ; P. H. Hall,
Brightlingsea; A. V. Phaisey, A. HE. Johnson, E. D. Lowes,
Swanley ; R. Fleming, R. 8. Cleator, E. V. Lawson, Fleetwood.
Mr. A. Harris, Chief Inspector of Navigation Schools, inspected
this class. Dr. E. 8. Russell, Director of Scientific Investiga-
tions to the Ministry of Fisheries, also visited the laboratory
during the teachers’ class and inspected the facilities for work.
36
Fish Hatching.
A stock of large plaice were collected in Luce Bay in
October, and in due course conveyed to Pie]. Adult flounders
were trawled in Barrow Channel towards the end of 1920.
The plaice and flounders both began to spawn on the 6th of
March, eighteen days earlier than in 1920, and continued to
produce eggs until 30th April. The last fry (plaice) were set
free on 24th May. Altogether 1,150,000 plaice eggs and
12,500,000 flounder eggs were collected and incubated;
1,000,000 plaice fry and 11,000,000 flounder fry were hatched
and set free.
Re-survey of Shellfish Beds.
The mussel beds of the Ribble, in the vicinity of Lytham,
were examined by Mr. W. Birtwistle and myself in July and
again in November, 1921. On the first date a topographical
survey of the sewer outfalls and their relation to the mussels
was made. On the second visit samples of the mussels were
collected and examined for sewage contamination. Reports
were submitted in each case and were published in the Report
of the Superintendent, Dr. Jenkins, for the quarters ending,
30th September and 31st December, 1921.
37
THE PLAICE FISHERIES OF THE IRISH SHA
BY
JAS. JOHNSTONE, D.Sc.; W. BIRTWISTLE
AND W. C. SMITH
CONTENTS
PAGE
PART I: Tue Pre-War PeEriop, 1908-1913 ae se sb 39
Introduction ace é Sct aie si 50 S00 5c 39
The area Sig etinated: p- 40; Nature and regulation of the
grounds, 42; Distribution of the various species of fish, p. 45 ;
Tables Land II, species of fish found, p. 46; Seasonal fisheries,
p. 49; Migratory fishes, p. 50; Long period fluctuations in
the fisheries, p. 52.
Methods of investigation noc ee ee tas as was 53
Treatment of the data ... dae ales si Ses iad as 55
Statistical methods, p. 56; Pearson curves, p. 58; Summational
curves, p. 60; Use of the same, p. 65; Measures of dispersion,
p- 67.
Lengths of the plaice caught ... Bie Tail
Tables III to XIII, Length Ereeuerisied i on ae anes dite
1908-1913, p. 73. Prevalent lengths, 85.
PART II: Tue Lire-History or THE PLAICE ane Ae née 88
The spawning grounds ... 506 50C 36h oe 306 506 88
The hatching and transformation stages... ane Ss ah 93
The first shore stages... Aa a ie a dis b3s 94
Food of the larvae and transformed plaice ... 596 a M6 95
Growth of the plaice during the first year ... pe ae re ee 96
The nursery grounds and their conditions... 506 ace oes 99
The rate of growth of the plaice aie 102
Tables XIV and XV, length freqnediion, se age-groups O- IV,
p- 104; Ratio of males to females, p. 107; Sizes at sexual
maturity, p- 108.
38
CONTENTS—continued.
PART I1—continued.
Migrations of the plaice
Plaice-marking experiments, p. 110; Age and the migration
paths, p. 126.
General remarks on the migration experiments
Growth-rate of marked plaice, p. 131.
PART IIL: Tue Pre-War AND Post-WaAR PLAICE FISHERIES
Fluctuations in the Plaice fisheries in the North Sea, English Channel
and Irish Sea ode te at
Fluctuations in Lancashire Tana p- 136; aHiuetie:
tions in the Mersey fishery, 1908-1920, p. 139 ; Table
XVI, length frequencies on the Mersey grounds, 1908-
1920, p. 140; Fluctuations in Liverpool Bay, 1909-1913, 1920,
p- 143; The Northern plaice grounds, 1920-21, p. 145;
Table XVII, length frequencies on the Northern grounds,
1920-21, p. 146; Proportions of the age-groups in various
years, p. 148 ; Table XVIII, length-frequencies for Age-group
III, p. 148 ; Table XIX, length- frequencies for Age-groups II
and III, p. 157; Composition of the plaice stock as regards
groups, p. 150.
Causes of the fluctuations
Table XX, length-frequencies of Apes pie in aN ee
trawl-net, Mersey grounds, 1908-1920, p. 154.
The post-war fisheries, 1920 BC
Tables X XI to X XVII, length- eas canes of sates seaaht on the
various grounds in the year 1920, p. 156.
The effect of the war restrictions on the fisheries
PART IV: PracricaL ADMINISTRATIVE QUESTIONS
The rate of exploitation
The impoverishment of a fishing region
Has there been impoverishment of the Irish Sea ann faienes ?
p. 170; Is there an accumulated stock ? Does increased fishing
tend ie make the plaice run smaller, p. 172; Did a stock of
plaice accumulate in the Irish Sea during the war years, p. 173.
The possible effects of legislative restrictions
The protection of the spawning grounds, p. 174 ; The question
of size-limits, p. 175; Effect of latter on smacks, p. 175; Effect
on the steam-trawlers, p. 175; Possible effects on the fisheries
of a size-limit, p. 176; The theory of restrictions, p. 178.
Cultivation is Ree bee Boe ses see sme See
PAGE
108
130
133
133
155
164
167
168
170
174
179
39
PART Vi.
THE Pre-War Periop, 1908-1913.
(1) Introduction.
This report is primarily a summary of certain fishery
investigations carried out in the Irish Sea region during the
years 1908-1920. Its object is to provide aseries of data which
can be consulted for the purpose of assessing the usefulness of
any practical legislative proposals as to size-limits or closed
grounds. It also endeavours to provide a picture of the present
condition of the plaice-fisheries on the fishing grounds men-
tioned below. If we had such a picture for the period 1870-
1890, the information so afforded would be of the utmost value
in the discussions that are now going on with respect to
questions of impoverishment, size-limits, etc. We think it very
useful, therefore, to summarise here what has been the outcome
of the investigations made by the vessels and officers of the
Lancashire and Western Sea-Fisheries Committee during the
last twenty years or so, as these observations will, at the least,
record the present conditions and give a basis for comparison
with those that may possibly be made some twenty or thirty
years hence.
The essential part of the report consists of the tables of
measurements, etc., that are given on pp. 73-84.
In addition to these we have added a summary of the results
of a series of marking experiments and some additional observa-
tions. In order, however, to present the general attitude
adopted a rather full discussion of the methods used has also
been written, and the general bearing of the conclusions reached
are also discussed on pp. 167 and following. The impression
obtained is that the time has not come for any legislative-
restrictive action in this part of the sea. That impression is,
however, personal to those of us who have been concerned in
carrying out the investigations, and does not necessarily
40
represent the opinions of the Committee. The reasons for our
opinion are given fully on pp. 167-179 of this report.
The Area Investigated.
The fishing grounds on which the observations and
experiments have been made are as follows :—
(1) The Solway Firth, including Luce Bay and Wigton
Bay, and the fishing grounds between the Isle of Man and the
coast of Cumberland. Permission to work on these regions was
kindly given by the Scottish Fishery Board and the Cumberland
Sea-Fisheries Committee.
(2) “‘Morecambe Bay.’ This includes the territorial
waters off the Lancashire coast, from the estuary of the Duddon
to Formby Point, and the offshore region out to the Morecambe
Bay Light Vessel.
(3) “ Liverpool Bay.’ This includes the estuaries of the
Mersey and Dee, and the adjacent sea out to the twenty-fathom
contour line.
(4) “Red Wharf and Beaumaris Bays.” This is the
region situated just off the coasts of Denbigh, Flint, Carnarvon,
and Anglesey, as far south as about Holyhead, and seaward
to about the twenty-fathom contour line.
(5) Carnarvon and Cardigan Bays.
(6) The inshore waters round Isle of Man. Work was done
there by arrangement with the Insular Fisheries Board.
(7) The offshore regions in general, about and outside the
twenty-fathom contour line.
The various geographical terms are employed rather
approximately and much in the same way as they are used
by fishermen. The whole region investigated is quite a small
one, but it is a typical, rich, inshore plaice fishing area of sea,
and it is one about which more is known than any other
similar region in the British fishing regions. The summary
that we provide cannot, therefore, fail to be of much interest
and practical importance.
42
Nature of the Fishing Grounds—their Regulation.
Most of the region investigated lies inside the three-miles’
limit, and trawling by steam vessels is everywhere prohibited
within this zone. In addition, trawling by any kind of vessel
is prohibited in Luce Bay by the Fishery Board for Scotland.
Trawling by motor-propelled vessels is permitted, by licence
issued by the Lancashire and Western Sea-Fisheries Joint
Committee, in Carnarvon and Cardigan Bays. There are
regulations with respect to the size of trawl-mesh, which is now
measured all round the mesh in the Lancashire and Western
District and in the Cumberland District. Trawling by steam
vessels is prohibited in the three-miles’ zone round the Isle of
Man. Vessels fishing for shrimps employ a trawl-mesh of
2 inches, and they are not supposed to retain any fish if these
are less than 8 inches in total length. The mesh of stake-nets
is also regulated, and is 7 inches measured round the four sides.
There are no restrictions on the times of the year when trawling
that is otherwise legal may be practised, and there are no
restrictions on the sizes of fish of any species that may be landed
and offered for sale.
Most of the whole region in question is what is called a
“nursery ground.” This is particularly the case in the Solway
Firth, in the estuary of the Duddon, in Morecambe Bay, and in |
the estuaries of the Ribble, Mersey, and Dee. Here there are
enormous tracts of sand-banks, which are laid bare at each
ebb-tide, and there are innumerable shallow channels through
these banks. The water is rather cold in the winter on these
shallow estuaries and rather warm in the summer—that is,
the extremes of temperature are greater in the bays and
estuaries than they are in the sea, just offshore. Sometimes
there is considerable ice formation in Morecambe Bay. The
higher temperature in the spring, summer, and autumn, and
the lowering of the specific gravity of the water by that coming
from the land are very favourable conditions, Water draining
43
down from cultivated land and from domestic sewerage systems
carries essential food substances on which many lower
organisms feed, and these lower animals and plants are the
food of others, which are then eaten by the young fishes which
inhabit the nursery grounds.
The tidal streams are unusually strong and tend to run
inwards to the Solway and Morecambe Bay from the channel
between Ireland and Scotland. The tidal streams coming and
going from St. George’s Channel also tend to and from the
“ Liverpool Bay ” region—that is, the coast containing the Dee,
Mersey, and Ribble estuaries. Off the mouths of these are
extensive sand-banks, penetrated by shallow channels. Plaice
and other fish spawn offshore and the eggs and developing
larvae are carried by the tidal streams to the grounds that we
have mentioned.
The extensive sand-banks in the bays and estuaries are
“alive ” with small Crustacea (Copepods), cockles, other small
bivalve shellfish, and small worms. In the channels, and on
the foreshores where the ground is rough there are enormous
accumulations of mussels forming “beds” or “skears.”
These animals, when young and small, are eaten by plaice,
dabs, flounders, and other fishes, and their presence and great
powers of regeneration are the principal reasons why the region
in question constitutes one great nursery ground. The supply
of fish-food, represented by bottom-living Copepods, worms,
and small molluscs, is almost illimitable, and could doubtless
support a much greater fish population than that actually
present on the nursery grounds. This fish population itself,
we have reason to believe, is only a small fraction of that which
is theoretically possible of existence.
In fact, such an area as that which we are now describing
is certainly one of the most “ productive ” that exists, being
capable of yielding far more organic food substance than any
equal area of cultivated land. The annual quantity of mussel-
44,
flesh, for instance, that can be raised on a suitable Lancashire
foreshore is greater by far than the quantity of beef or mutton
that could possibly be raised on the same area of the best
grazing land.
This is the general nature of the North-west inshore fishing
grounds, but some of the sub-regions differ from the above
description. Luce Bay is such a nursery ground (in certain
places), but it also contains large numbers of big plaice, up to
over 60 cms. in length. Something in the nature of the Bay,
and its water and food supply, may be associated with this
remarkable distribution, but the main factor is preservation.
The Bay has, for a long time, been closed against trawling by
the Scottish Fishery Board, and the amount of other fishing
(by “ gill-nets ””) that goes on is insufficient to deplete the area
of the large fish.
The fishing grounds of North Wales, lymg just off the
coasts of Carnarvon and Anglesey, between Great Orme’s Head
and Point Lynus (Conway Bay, Beaumaris Bay, Red Wharf
Bay), are not nurseries to the same extent as are the grounds
mentioned above. Here medium and big plaice are caught,
principally during the months of October to January. There are
nurseries in Carnarvon and Cardigan Bays, but not to the same
extent as off the Cumberland, Lancashire, and Cheshire coasts.
Medium to big plaice may be caught in the great Welsh Bays
at the beginning of the year and in the summer and autumn
months.
¢
What we may conveniently call the “ offshore grounds ”
are situated outside the twenty-fathom contour line on the
English side and between this and the Isle of Man; also out
from the same depths in “ Channel Course ”’* and St. George’s
Channel, and between Cumberland, Isle of Man, and the South
Coast of Scotland. Plaice occur over most of this region, but
* «Channel Course ”’ is the sea in the neighbourhood of the general track
followed by vessels entering Liverpool from St. George’s Channel.
45
in much smaller numbers than on the zone of sea within the
twenty-fathom contour line. In fact, we may neglect most of
the Irish Sea outside this limit as a plaice ground—though it
would, of course, be difficult to give statistical data demonstrat-
ing this. By far the greater part of the plaice caught come
from the shallow water less than twenty fathoms in depth.
Distribution of the Different Species of Fash.
Even in such a small area as that which we are
considering—it is all included within 3° of latitude and 2°
of longitude—there are quite noticeable differences in the
predominant kinds of fish present on the fishing grounds. This
is Ulustrated by the following tables and graph, which represent
the results of a number of fishing experiments made in the Firth
of Clyde and Luce Bay (by permission of the Fishery Board
for Scotland) as well as in the Irish Sea. The experiments
were rather rough ones, being made at different times and by
different vessels, so that the results are not precisely com-
parable. Still, | have no doubt that very much the same
general ratios would be obtained even by carefully standardised
trawlings.
46
Table I. Results of Trawling Experiments carried on during
the months of Feb.-May, 1898-1904 and Sept.-Nov., 1908-13.
| West | |
Firth from | Offshore} Cardigan | Liverpool | Luce
Kind of Fish, | of | Isle of | grounds.) Bay. | Bay. Bay.
| Clyde. Man. | |
| | |
Witchy ceteasevcesrectes: | 4,164 430 Tie eens see ra
Blaicenecrsssasntecsccess | 1,093 27 | 346 1,203 | 3,544 4,548
Dab pa eereccngoes eon | 354 Ome a deni 574 | 2,920 1,015
Lemon Sole ......... 119 34 60 40 we 28
Stolle)» Aeandceacosusssoec 116 10 509 411 18 ae
Brillecsactsccecssecsss 33 | 1 42 42 | 7 21
Mlounder y eececceeces: 14 | 638 36 107 PAT
Meo rina aicecceeerscct 9 152 8 BH
AIA Goonsnagsdoadoo 6 2 2 4
Longrough Dab... 5a¢ 4 ee BE Bcc
TBINGSIG KS Seucnoobonee 1,121 65 1,427 we 99
Hake sees ceeceiisesectilc 148 4 ae Spe 500
NVI EIn ene esc aeecs 70 | 493 940 154 ie a
(Olo%6 |e Sa smaendesooosdeoadc 41 13 141 2 116 70
GLIMEAN codsacaosascode 42 4 ] 550 50 22
IDTV soonocqonnp5b00n00> 8 4 3 50
ollackwecenss-sccesse Soa | 4 1 iE ee 12
Poor Cod Wa-ee.- 2-2 ame ALU 39 36 an ace 1
Grey Gurnard ...... 759 466 519 115 101 30
Red Gurnard _...... 47 | 27 190 7 ia 4
Yellow Gurnard...... 1 9 34 27 16 20
Gonmer tierce |) el ial es 1 2
TER s. iGaeqnbdgndbdnodue: 347 123 434 761 669 610
Sleaitetemerescccseacseras 10 6 130 20 108 3
John Dory, | ences: 1 | ees =e 1
AN AWAIT? gaoodbosnono|ce 300- |) 800 Doe 400 B00 1
IBIGYTANEYE cooeopoonanoooe 508 me dot ee BOC 12
No. of hours’ |
1D RWAMUAYE?! srooecoae la) LOS 45 | 242 | ai 45 27
Mean depth ......... | 22 32 | 21 12 | 6-5 7
| = lice =a
Total edible fishes 8,507 1,996 | 7,208 3,404 7,706 6,431
| a
No. of Species ...... 22 22 Ger 2oe| 14 | 12 | 19
47
Table Il. The same data as on p. 46, but expressed as numbers
of fish caught per hour’s trawling (If less than one fish results
from the calculation the species is omitted).
|
West
Firth | from | Offshore! Cardigan | Liverpool | Luce
Kind of Fish. of Isle of | grounds.| Bay. Bay. Bay.
Clyde. | Man.
All edible fishes... 83, | At 30 83 171 239
\WAKWG 1). pcacndeodeocoodcoc 40 10 aes as eee sat
IPIBNES. opedeanenbocaubscs 11 1 1 29 79 168
Dalby isacccscsessesitesce 4 1 7 14 | 65 38
Lemon Sole ......... i 1 ws 1 as 1
SOI | Vasorieponsedcscoode WS cee 2 10 ae eee
IBTUD Soe ccdesesaecases 500 AG is 1 adc 1
IOUNG ET ser eceeeise 200 Spc 3 | 2 1
Wigan) Gaceocs6ccosc0 so. 3 was ce
[Haddocks \rse-cereece 11 1 6 aa 2
FLBCON <.30--esncvecoess ie de :
DWIRICIN Gos fcchssveceeee ee) eh 4 4 ie
(Cio | Caen een | 1 3 3
Woalfishin. ontscccccuer oo aes aE 5 | ot 1
Grey Gurnard ...... eal 10 2 3 2 1
Red Gurnard ...... oso | I 1 tae
Yellow Gurnard...... Ato | cok sai 1 1
TRAY, Jenescisvesdsescers c 3 2 19 15 23
SKA bees ssse seems cose 1 1 2
Mean depth ......... 22 32 21 1) 65 7
The first of the above tables gives the actual numbers of
hauls and hours of fishing, and the numbers of fish of different
species that were caught. The second table simplifies the
former one in that it gives the numbers of fish caught per
hour’s trawling, in all the trials, and neglects all results in which
less than one specimen—on the average—has been taken. A
further simplification is rendered possible by the following
diagram, which takes account only of about two-thirds of all
the fish caught—that is, it gives us a fair idea of the prevalent
kinds and abundance of trawl-fish present in our whole region.
48
as Pigee| Dab
Hie. 2.
Note, then, that whiting, gurnards, and witches are
characteristic of the deeper grounds to the West and South
from Isle of Man, witches, haddock, and plaice of the Firth of
Clyde,* and dabs, haddock, whiting, and flounders of the
offshore grounds outside the shallow coastal waters of Lanca-
shire. We find plaice, rays, and dabs are characteristic of the
fishing grounds in Carnarvon and Cardigan Bays, and plaice
* That is, the Clyde between Stranraer and the South of Arran.
49
and dabs in Liverpool Bay. Luce Bay, it will be seen, is far
more characteristically a plaice ground than any of the others.
Some qualifications, with regard to this statement of
distribution, will be found below.
Seasonal Fisheries.
The various fisheries are all seasonal ones.
The great plaice fishery is that off the coasts of Lancashire
and Cheshire in the summer and autumn months. Sometime
about May or June plaice become abundant just off the mouth
of the Ribble Estuary, and then this abundance becomes
extended to the grounds North and South. About the begin-
ning of August the fish usually appear in great numbers round
about the banks off the entrance to the estuaries of the Mersey
and Dee. By November these fisheries begin to fail.
About the same time, or even earlier, plaice become
abundant off the coast of North Wales, anywhere hetween
Rhyl and Red Wharf Bay, on the north of Anglesey. This
winter fishery ends about December or January, sometimes
very abruptly. Then good catches of fairly big plaice may be
obtained inshore in Carnarvon and Cardigan Bays.
After that there follows a period when plaice are relatively
very scarce everywhere. Some, of course, are always caught
wherever there is trawling, but, in comparison with the well-
marked summer and autumn fishery off the Lancashire coast
and the equally well-marked North Welsh winter fishery, the
plaice are very scarce. About the month of January medium-
sized and big fish appear on the banks to the north-east of Isle
of Man, and there may be a good deal of trawling there. A
little later, however, these grounds may become “as bare as
a bilhard ball.” Followimg that again the bigger plaice are to
to be found on the ground called the “‘ Slaughter,” just off the
mouth of the Solway. Here they spawn and the shoal disperses.
Sometime about March and April, then, large numbers of plaice
D
50
disappear from the Irish Sea fishing grounds, and there is always
much speculation among fishermen as to where they go. There
is little doubt that they ‘“‘ dawk ’”—that is, bury themselves in
the sand in the channels offshore and among the sand-banks.
Here they remain during the period of the year when the
temperature is at or little above its minimum value, and when
food has become scarcer than usual. Noting all these facts
as to the seasonal nature of the plaice fishery, and comparing
them with the results of the marking experiments—to be stated
on pp. 110-132 of this report—we have little difficulty i
making a general picture of the migrations of plaice in the
Trish Sea regions (see p. 130).
The Migratory Fishes.
It will be noticed haddock are mentioned in the tables on
pp. 46-7, though if a similar series of experiments were to
be made at the present time this fish would be much scarcer—
and it might not be represented at all in some of the areas. A
number of species are migratory ones, entering the region we
are considering and then moving away again. Some of these
species come back every year with a certain amount of
regularity and others only return after a more or Jess prolonged
period. Although we are dealing mainly with the plaice in
this report it may be useful to say a few words about these
migratory species.
Hake.
Specimens of hake may be obtained now and then from
most parts of the Irish Sea, but the fish is only (relatively)
abundant to the west and south of the Isle of Man in the autumn
months (usually July, August, and September). It migrates
up from St. George’s Channel, in the South, with the rising
temperature of the sea and moves southwards again when
the temperature falls. The fishery is, however, not a very
important one.
51
Sea-Perch (Labraz lupus) and Mackerel.
So also with these fishes. They come into the Irish Sea
at variable times, but generally about May or June, and they
stay till about August and September. Thev also come up
from the South and retreat back there again. Hake, sea-perch,
and mackerel we may regard as southern fishes, and take their
northern limit of distribution to be some particular isotherm in
the sea. This isotherm, whatever it may be, changes from
South to North as the summer advances and then changes
back to the South as the sea temperature begins to fall, rather
rapidly in September and October.
Ferri ng.
This is a well-known migratory species, but the conditions
that rule the movements of the fish are very complex and are
not clearly known as yet. There are two main herring fisheries
in the Irish Sea area: (1) the Welsh winter, and (2) the Manx
summer fisheries. The Welsh winter herrings appear in
Cardigan Bay in October and the shoals gradually move to the
North as the season advances, disappearing off the North Coast
of Anglesey sometime in January. The fish are mature ones
and are “ full’? when they first come on the coasts; later on
they spawn, and by the end of the season they are usually in
the spent condition.
The Manx herrings are sometimes found off the coasts of
the Island as early as February, but not in abundance. About
May they begin to become abundant and are to be caught on
the west, south, and east of Isle of Man. In July to September
they spawn, and soon after that the shoals disperse and the
fishery comes to an end.
The Sprat.
The sprat is found everywhere along the Lancashire and
Welsh coasts and in the Solway, but during the summer months
it is mainly immature fish that one sees. About October
52
mature sprats begin to shoal and are abundant enough to
provide the material for a fishery. They are probably to be
found all along the coast, wherever suitable gear may be used,
but the only fishery is that prosecuted at Morecambe during
the period October-March. The fish are mature ones about to
spawn. Just before spawning they disperse and the fishery
comes to an end.
The Cod.
Cod are found over all the region and generally at all
periods of the year, but there are local fisheries where the fish
is more abundant than elsewhere. About March fair catches
are made off the coast of Cumberland and even further South,
and about the same time there is a fishery off the West Coast
of Isle of Man. In both cases the migration is a spawning
one and the fish are full-roed ones. At the best, however, the
cod fisheries in the Irish Sea are not of very much importance.
The fish is a northern one, and this is near its southern limit
of range.
There are, of course, other migratory species of less
importance—thus, whiting move about in much the same way
as the cod. Large numbers of whiting, cod, and other species
are to be found in the early stages on the nursery grounds
during the summer and back-end. (rarfish (Belone) come in
from the South during the summer and the long, rough dab
(Drepanopsetta) comes down from the North in the early spring.
The sole is, to some extent, a migrant, having its place of
ereatest abundance to the south of our area. Some species
of ray are also periodically migratory.
Long-Period Fluctuations.
Two species (at all events), the herrmg and haddock, are
very capricious in their movements. The Welsh and Manx
herring shoals are constant in their appearances and disappear-
ances, but there have been other herring fisheries which come
58
and go. About 1890 and later herrings appeared off the coasts
of Lancashire from Morecambe Bay to the Mersey Estuary,
and were fished for, by drift-nets, in the latter area as far up as
near the entrance to the Manchester Ship Canal. Before that
time there was a fishery near the mouth of the Solway, and the
“ Parton Herrings,” taken just north of Whitehaven, were well
known and highly esteemed. Since then, and until last year
(1921), these fisheries did not exist and only occasional herrings
were taken. In the winter of 1921-22 the herrings came back
to the Cumberland and Lancashire coasts in fair abundance
and were taken at Maryport, at Morecambe, in Morecambe
Bay, and all down the coast as far as Great Orme’s Head.
Thus, there has been a period of about thirty vears during
which the fish disappeared almost entirely. Before the ’nineties
of last century there were other long-period fluctuations—thus
somewhere about 1774, herrings were abundant in the estuary
of the Dee—and doubtless elsewhere on the Lancashire and
Cheshire coasts. In 1840, they appeared in the Mersey. No
definite information is, however, now obtainable with regard
to these fluctuations.
Haddock came into Liverpool Bay in great abundance
about 1890 to 1895. Since then they have been practically
absent, only an occasional specimen being taken.
(2) The Methods of Investigation.
The work was begun in 1908 and the methods employed
were, briefly, as follows :
(a) Trawling experiments were made on the various
grounds by the L.W.S.F. patrol vessels “John Fell” and
“James Fletcher,” and also by some of the police cutters.
All the plaice caught were measured immediately after the net
was cleared. Lengths were recorded in centimetre groups,
all fish which were over » and less than n+1 cms. being
recorded as » -5 cms. The principal grounds sampled were
5A.
Luce Bay (in October, November, and December), the
Cumberland coastal grounds, the ‘‘ Nelson Buoy” grounds,
the “Mersey Estuary,” the “ Red Wharf-Beaumaris Bay ”
region, Carnarvon and Cardigan Bays.
(b) Trawling experiments were made continuously from
1890 to 1920 by the sailing vessels employed on police work
in the Mersey Estuarine area. All these experimental hauls
were made by the same officer, Capt. George Hccles, a highly-
experienced fisherman. Two series were made, one with the
ordinary smal] trawl-net of 6-inch mesh, and the other with
the ordinary shrimp-trawl net of 2-inch mesh. Some other
similar series of bauls were also made in other parts of the
District.
(c) Comparative hauls with trawl-nets of 4-inch, 6-inch,
and 7-inch meshes were made.
(d) Samples of the plaice caught on the various grounds
were regularly sent to the Liverpool laboratory. These were
examined in detail :
They were measured as above and sorted into groups of
n to n+1 cms.
The whole lot of fish in each group was weighed to the
nearest gram and the total weight was divided by the
number of fish. Average weights were so recorded.
The length-weight coefficient “k” was then calculated
(see Ann. Rept. Lancashire Sea-fish. Laby. for 1911, p. 17).
Each fish was dissected; the sex was determined, as
well as the stage of maturity ; the age was determined by
inspection of the rings on the earstones and the food contents
of the stomach and intestine were often identified.
(e) Observations were made by the ‘ Fish-Measurers,”
W. C. Smith, A. E. Ruxton, and G. Sleggs, on board steam
trawlers, smacks, and _ half-decked trawlers. This work
began in 1920. It was mostly restricted to the offshore
grounds and to the shallow water area of the Solway Firth.
55
(f) Marking experiments were made. These began in
1906 and were carried on until 1913. Twe areas were seen to
be of much importance: the grounds off Nelson Buoy and
those in Red Wharf and Beaumaris Bays, and most of the
experiments were made there. In 1920 and 1921 the experi-
ments were renewed and plaice were marked on the grounds
between Isle of Man and the Solway Firth. In all cases the
English form of mark was used ; at first the bone button and
brass label, and later the vulcanite buttons and labels.
(g) In 1921 the larval and post-larval plaice were
studied. Catches were made by means of the Lancashire
“push-net,” which is used to catch shrimps, being pushed
along the sea bottom, in water of two feet or so in depth, by a
man wading. The flat fishes collected in this way (from the
Cheshire coast and the coast of the Isle of Man) were identified
and measured and their food contents were recognised. Larval
and post-larval plaice from the Hatchery at Port Erin were
also collected and their food was examined.
(h) Other investigations (Embryogeny, variability) were
contemplated, but have not so far been adequately made.
(3) Treatment of the Data.
Not very much was to be made out of a direct comparison
of the numbers of fish caught per hour’s trawling, on the
various grounds, and at different times. The standardisation
of the fishing gear and vessels and of the canditions under
which the experimental hauls were to be made, were too
difficult. In no case have we had, at our disposal, a vessel
used exclusively for scientific research, and all the work had
to be done on board the police steamers and sailing boats, or
on board steam trawlers, smacks, and inshore trawlers. It was,
of course, very gratifying that the L.W.S.F. Committee allowed
us the use of their vessels, and we are also much indebted to
the owners and masters of the commercial boats, whe allowed
56
the fish-measurers to go to sea with them and make records of
the fish caught. Still in no case were we in control and fully |
able to choose the grounds and times for the hauls. Scientific
work on board the police vessels had, of course, to be dependent
on the nature of the official duties that were to be performed.
In the circumstances the results that were obtaimed are very
satisfactory.
One can, of course, make certain conclusions of value
merely by comparing average catches taken at different times,
and on different grounds, with each other. No doubt these
experiments do give us rough general pictures of the abundance
of fish from time to time and, so far as they go, they must
represent the experience that an observant fisherman would
acquire. Thus the tables on pp. 46-7, giving the relative
abundance of the different species of fish on the various
grounds, are certainly to be regarded as representing the
natural conditions in an approximate manner. So also, the
series of hauls made in the Mersey by Capt. G. Kecles, give
some very valuable information. Too much, however, must
not be made of the ordinary periodic trawlings on which the
present report is based, as representing variations in abundance
from year to year.
What has been done has been to seek to get the information
we require by a study of the measurements of the fish them-
selves, rather than by mere counts of the numbers taken per
haul. These relative lengths, ages, etc., are independent of
the actual numbers of fish taken. It will be seen that they do
give us valuable and, we believe, reliable data. Combined with
the results of the fish-marking experiments and the information
siven by the official statistics, they enable us to deduce
conclusions that are of value for the administrators.
The statistical methods employed.
When the measurements of the fish sampled are arranged
as follows :—
57
Mean length = 10-5, 11-5, 12-5, 13-5, ete., cms.
Nos: caught = 2, 9, 133,46, ete:
we obtain a series called a ‘* frequency distribution.” There
are many ways of forming such distributions from the same
data. The ‘ mean-lengths ” 10-5, etc., represent the middle
points of the groups of measurements, that is 10 to Ilsems.,
11 to 12 ems., ete., but these groups might have been 10 to 12,
12 to 14, 9 to 11, 11 to 13, ete., or they might also have been
4 to 44 inches, 44 to 5 inches, etc., or even 4 to 5d,
5 to 6 inches, etc. If we were to make such alternative series
of measurements from the same sample of fish and then plot
curves from the various distributions we should not get
eraphs of the same form. Nor should we get quite the same
averages and other statistical results. It is convenient to
measure the fish in centimetre groups, but such a method has
20 superiority over any other arrangement except its con-
venience.
If the series of measurements is a very big one—say
several thousands of fish—it will not matter much what way we
express the data. But every now and then small samples,
50 or 100 fish, say, must be studied. Therefore we require
some way of avoiding the errors which arise because of the
alternative methods of grouping the measuremeats.
This means that the crude distributions must be
“smoothed”? in some manner. In general, a series such as
the above one is irregular and these irregularities affect
whatever form of average we adopt. Hf we calculate the
latter an1 then re-measure the fish and arrange them in a
new way we may get different irregularities which affect our
averages (or other statistical conclusions) in different ways.
Which results are we to accept? In social and_ political
controversies we do all these things and then accept the
results that are the most welcome ones! But this kind of
statistics is that which “ can be made to prove anything,” and
we must avoid it “like the plague.”
58
“Smoothing” might be effected by taking overlapping
averagcs. Thus, instead cf the frequency, 5, at mean length
2+5 ;
11-5, in the above example we might take a = vss Ole:
instead of 13, at mean length, 12-5, we might take
5 + 13+ 46
)
some cases this method has an approved basis; it means that
== 21:3 and so on, all through the series. In
we are generally in doubt that any fish we measure is properly
measured : it may really belong to the group in front, or that
behind the group in which we have placed it. This is so with
a number of fish in every sample. If one is very near 11 ems.,
say, it may be really a little less than 11, so little less that
our necessarily hurried methods may not enable us to be
sure. But it 1s only a few of the fish about which we are in
doubt, in this wav. That means that we ought to employ a
smoothing formula of this kind,
(Bornes ee
Qe
where m is a small number, say 2 to 5.
Pearson Probability Curves.
The really scientific way to smooth such series as we have
is to calculate a theoretical distribution and then use this instead
of the crude series obtained by the measurements. Pearson
curves are based on the theories of probability. The different
results that are got in playing games of chance are explained
by assuming that these results are due to the operation of a
ereat number of small causes. The number of sixes one gets
on throwing a dozen dice at the same time, or the number of
heads we get when we throw a dozen pennies into the air, are
chance effects due to a great number of small, mdependent
causes, which are usually beyond our powers of control. The
theory of probabilty enables us to calculate such chance results
beforehand, and the calculated result agrees surprisingly with
59
the actually-observed result, when the number of trials is
fairly large. Event when the chance results are due to the
operation of a number of small causes, some of which can be
controlled (say the “ loading ” of the dice, or the cutting away
of the metal from some of the sides of a “* put and take ” top),
the theory does not fail us. When the causes of variation are
quite beyond our control we obtain a symmetrical curve of a
certain mathematical form, and most biological variation
curves approach more or less closely to this form (the normal
curve of error). Human biological inequalities (sav variability
in stature, or in the ability to pass an examination) come very
close to this symmetrical form. On the other hand, social
inequalities (say the annual value of the house a man inhabits ;
the income on which he pays tax, etc.) are entirely different,
for the curve of variability in such cases is an asymmetrical,
* J-shaped,” exponential one. The meaning is that the causes
of wealth and poverty have come under our contro], and that
the control endeavours to bring about the observed form of
inequality.
In many of its applications (insurance and actuarial
calculations) the theory is sound. When it is applied to the
results of the study of organic variability it must also be
regarded as sound. Obviously, when we apply it to finding
out how much we are to qualify the results of taking a sample
of something we are also on the right lmes. Now these observa-
tions which we study here are samples. There are some
millions of plaice on a certain fishing ground and we want to
know their average length as well as the numbers that differ
from the average by definite gradings above or below the
average. We take a sample of, say, 1,000 plaice from this
population and measure them and find the average and the
variations from the average. But we cannot be certain that
our sampling has been representative : some of the size-groups
are always over-sampled and others are under-sampled.
60
Repeat this sampling again and the same misrepresentation
occurs, but it is different groups that are under- and over-
sampled.
If this were all we could apply Pearson curves to such
data as are here given. But the theory supposes that the
population that is sampled is an homogeneous one in respect
of the characteristic that we measure. One could not legiti-
mately measure the stature of all the individuals in a crowded
church, say, and then base a Pearson curve on the results.
A number of the people are full-grown men, others are full-
erown women, and others again are boys and girls of different
ages. Thus there are groups in this church population, and the
mode of variability from the average is not the same in every
group. We ought to measure and classify the full-grown men
separately from the women, etc., making a separate curve for
each. The assemblage is an heterogeneous one.
All fishery samples are, in general, heterogeneous, consisting
of fish of one, two, three, etc., years of age. We find this by
examination of a sample. It is, in general, quite impracticable
to attempt to separate the sample of plaice caught and measured
into its year-classes. Therefore we cannot (in general, again)
apply the method of Pearson curves to treatment of the
statistics, and this is fortunate, in one sense, because the
arithmetic that is mvolved is “colossal.” Still there are
samples in which one year-class may preponderate so greatly
as to smother all the others. So some of the distributions in
this report have been “ Pearsonified,’ with the object of
illustrating this discussion.
The Construction of Summational Curves.
The method that has been adopted has been to smooth
the observed frequency-distributions by making summational
series from them. Then all the information required is obtamed
from the latter curves. The methods actually used will best
be described by an example.
61
Example : Table V, June, 1908-1913.
| |
(1) e | @ Qo Gi (6)
Mean
length. i Halts Sa Wee y Ly
13-5 1 0-5 | 1000-2 ae
14:5 iy 6-4 999-7 2-1 998-8
15:5 39 20-7 | 993°3 21-6 996-7
16°5 106 56-2 972-6 64:4 975-1
17°5 205 108-8 9164 | 111-9 910-7
18-5 304 161:°3 807-6 | 143-0 798:8
19-5 263 139-5 | 646°3 149-9 655°8
20:5 231 122-6 506°8 136-7 505-9
21-5 228 121-0 | 384-2 112-6 367-2
22-5 183 97-1 263-2 85:7 256-6
23-3 124 65:8 166-1 61:3 170-9
24-5 67 35-5 100-3 41-6 109-6
25-5 45 23°9 64:8 27-1 68-9
26:5 24. 12-7 40-9 17:0 40-9
PA 5) 20 106 28-2 10-4 23:9
28-5 9 4°8 17-6 6-2 13-5
29-5 14 7:4 12:8 3:6 7:3
30:5 5 2-7 5-4 2-0 3:7
31-5 3 1-6 | 2-7 1-1 1:7
32:5 *4 1-1 1-1 0-6 0-6
1,885 1000-2 998°8
The plaice have been grouped into one cm. classes, 13 to
14, 14 to 15, and so on: Col. (1) gives the middle points of these
class-ranges ; Col. (2) gives the actual numbers of fish measured
and belonging to each class-range, and Col. (3) gives these
frequencies expressed as numbers per 1,000. Thus all the
series given in this report can be graphed on the same scale,
and the graphs can be superposed for comparison. But the
actually-observed frequencies are necessary whenever we
require to find the “ probable errors,” so they must be stated.
Col. (4), “ =f°/,.,” gives the results of the process of summa-
tion: thus the entry, 17-6, opposite the length, 28-5 ems., is
the sum, 48+ 74+ 2-7+ 1:64 1:1, of the frequencies
opposite 17-6 and below the latter. In this case the summation
begins at the bottom of the column, but it might as well
begin at the top. The entries in Col. (4) are to be read in this
62
way: 1,000-2 °/.. fish are 13 or more than 13 ems. in length ;
999-7 °/,, are 14 or more than 14 ; 993-3 °/,, are 15 or more than
15 cms., and so on. Or, again: 263-2 °/,, plaice are 22 cms.
or over 22 cms. in length and 506-8 °/,, are 20 or over 20 cms.
long. Therefore 506-8 — 263-2 = 243-6 (that is, about one-
quarter of the entire catch) are over 20, but less than 22 cms.
long.
Col. (5) in the table, “y,’ represents the theoretical
frequencies as calculated by Pearson’s method of curve-fitting.
Now let these theoretical frequencies be summed in the same
way as Col. (3) has been obtained : we thus get Col. (6), “ Xy.”
It will be seen that this is very similar to Col. (4), which gives
the result of the summation of the crude frequencies. The
crude Sf’s are more like the theoretical }f’s than the crude
J ’sare like the theoretical f’s, and this is because, in the process
of summation we have automatically got rid of the errors of
random sampling—or, at least, to some extent. How this
comes about is easily seen: if one class, say the fish of 18 to
19 cms., 1s over-represented in the sample, then all the other
classes will, on the average, be under-represented. Now in the
summing we add together at each stage over- and under-
sampled classes, and so the error of random sampling, apparent
in the frequency series, tends to disappear from the summa-
tional ones. Therefore, in graphing these various columns it
will be seen (fig. 3) that the crude and theoretica] summational
series are nearly the same.
From the summational series, made in this way, smoothed
frequency series can easily be constructed. First of all the
summational series must be graphed on a fairly big scale. The
curve must not be drawn free-hand, but by means of some
device that enables us to lay a spline, or steel spring, evenly
among all the points plotted. The curve should pass as nearly
as possible to all the points, but without necessarily passing
actually through any of them. It should be drawn by running
63
a pencil trace along the spline, and the trial curve so obtained
must then be inspected. When the points are connected by
short, straight lines it will be seen that there are a number of
polygons, some situated above the curve and others below it :
the combined area of the polygons above the curve should be
equal to that of the polygons below the curve. If this is not
so the curve should be redrawn.
/20
80
Scale fer summational curve
ce ie | bras.
The changes of curvature should be as gradual as possible.
We must first resolve whether the summational curve is simple
or compound. Usually it is simple—that is, it should present
one part which is all concave to the horizontal axis and another
part which is all convex (as in Fig. 3). | There will be a portion
which has no sensible curvature—that is, it looks like a straight
line sloping in one direction or the other, according to whether
the summation begins at one end of the distribution or the
other. At the ends the summational curve is sensibly parallel
to the horizontal axis. Sometimes there is a hump on the
summational curve, formed by several pomts—say 3 to 6.
When this is so the curve should endeavour to follow these
64
points, and in that case it will be seen that there are now
two places where the summational curve is concave, and other
two where it is convex to the horizontal axis. The frequency
series from which the summation has been made must now be
regarded as consisting of two simple, superposed series.
In doing all this we are adopting a definite formula of
interpolation. In making the smoothed curve pass evenly
among all the plotted points we are making its total area equal
to the total area of the polygon formed by connecting the
plotted points by short, straight lines: in the Pearson method
of calculating a theoretical curve we must first assume that
the total unsmoothed frequency shall be equal to the total
smoothed frequency. Further, the equation of the curve which
is thus calculated by Pearson’s methods is graphically repre-
sented by a certain form, and this form, for our smoothed,
summational curve, is given by the line of gradually changing
curvature, which is everywhere as near as possible to the plotted
points. The elasticity of the spring (which we assume to be
the same everywhere in it—not always the case, however, in a
much-used one) confers on the curve this gradual, unforced
change of curvature.
The actual, smoothed curve, which is to be used further, is
drawn with a ruling-pen filled with red ink, and obviously a
fine trace is made. The points where the curve intersects the
vertical scale lines of the graph paper are now pricked and the
ordinates are read off on the vertical scale. These are written
down to replace the unsmoothed ¥/ series. This smoothed
series is next differentiated so as exactly to reverse the process
of summation, as it was carried out on the unsmoothed / series,
and the result is a smoothed, frequency curve. It is not quite
smooth, however, because it is rather difficult to read off the
ordinates very precisely on the vertical axis. There is never
any difficulty, for all that, m drawing a smooth, frequency
curve through the points found by this process, for we can
65
easily find three other important characters of the curve—its
maximum and its points of inflexion.
Very often the smoothed, frequency curve so found is very
like the Pearson one which can be calculated but it is often
significantly different in form. When this is the case the
smoothed curve found graphically is, we think, to be preferred.
Undoubtedly, there are plaice frequency series which do not
give a Pearson curve with sufficient ‘‘closeness of fit” to
satisfy the criterion proposed by the statisticians, and this
may be the case even when the measurements are numbered
by thousands. (Obviously the law of variability is not that
stated by Pearson’s fundamental, differential equation with
four constants.)
Use of the Summational Curves.
These curves can be used to obtain the numbers of fish
between any two sizes. This is possible from the summational
series themselves when the sizes in question are whole numbers
of centimetres (or otherwise the numbers representing the ends
of the groups or classes). From the curve, however, we can
interpolate graphically and find the frequency between any
limits whatever—the method is an obvious one and is illustrated
onip: 69:
The Mode or Maximum.
This is the position of greatest frequency—the peak or
hump of the frequency curve. It can be found graphically as
follows :—
A fine, straight line is scratched on a strip of transparent
celluloid (a set-square, for instance) and the extremities of the
line are neatly pierced by fine holes made with a needle. The
set-square is laid on the graph, scratched line downwards, and
then it is rotated, so to speak, on the curve. Where the latter
changes from convex to concave there is a ‘‘ point of inflexion,”
and here the tangential line will cross the summational curve.
E
66
The set-square is now held in this position and ¢he apertures
at the ends of the line are pierced so as to make points on the
graph paper. The set-square is taken away and a fine line in
red ink is ruled on the graph: this will appear to coincide with
4.
Hies. 4 and 5:
that part of the summational curve which is sensibly straight.
By inspection we find the points where curve and tangential
line begin to diverge, and half-way between them we may take
to be approximately the point of inflexion. This point is
marked and a perpendicular is dropped from it to cut the
horizontal axis. This latter point of intersection, read off on
the scale of lengths, gives the abscissa of the mode, or maximum,
of the frequency curve.
The Poanmts of Inilexioen:
Let the summational curve be supposed simple. There
will be two places on it where its curvature is greatest, and these
can be found graphically as follows :—
Rule two parallel lines, about 1 cm. apart, on a transparent
set-square and rule another line perpendicular to both at about
the mid-points of the parallel lines. Graduate the lower line
in mms. Rotate the ungraduated line on the set-square on
the summational curve at the places of greatest apparent
67
curvature and find the point where the chord, as given on the
graduated line, is of least length. This point is approximately
the portion of greatest curvature. Drop a perpendicular from
this to cut the horizontal axis and the point of intersection,
read off on the scale of lengths, will be the abscissa of the point
of inflexion on the frequency curve.
Measures of Dispersion.
There are a number of such measures—for instance,
Standard Deviation, Probable Error, Interquartile Range, Semi-
Interquartile Range, etc. We cannot properly speak about
“the length” of the plaice inhabiting any sea area in any
particular period of time for these lengths may be anything
between the extreme lengths actually observed. But we see
that all these sizes of plaice do not occur with equal frequency—
for instance, the table on p. 61 shows that the plaice on the
area in question, and at the particular time, ranged from
13 to 33 ems. in length. Nevertheless, about 25 per cent. of all
were over 20, but less than 22 cms. in length. Evidently, then,
we attach importance to a limited range of lengths, the ends of
which are situated somewhere on each side of the maximum
of the distribution: this range gives us the prevalent length of
the fish at that time and in that area.
The commonly used measures of dispersion are con-
ventional ranges of this kmd. The “ probable error ”’ and the
“interquartile range ” are supposed to represent a short range
of lengths near the mean length (or near the mode, or near the
“median ”’), such that within this range are contained one-half
of all the fish in the sample. The “ probable error” is cal-
culated from the “ standard deviation,” which is calculated on
the assumption that the frequency curve representing the
distribution is what is called the “ Gaussian” one. It seldom
is in any of the distributions that we have found. Therefore
the use of the standard deviation and probable error has no
theoretical justification, and, indeed, it may be very misleading.
68
The interquartile range is calculated by finding the
“median” and “ quartiles.” The arithmetic is simple and
easy. The method is applied to the crude frequencies and it
is therefore affected by the errors of sampling and by the errors
that arise from grouping. If different methods of grouping
are adopted—in the cases of small distributions—different
medians and quartiles are obtained, and any one of them, found
by different methods of grouping, is equally probable. If we
group only in one way we get only one interquartile range, but,
obviously, there are other equally admissible interquartile
ranges which we have not calculated !
What measure of dispersion is to be adopted? This
depends on the plan of the investigation for the measure in
question is only a means to some conclusion or other. Here
we adopt the measure called the “ shortest half (or two-thirds,
or three-quarters) range.”
The Shortest Half-range.
The total area of the frequency curve (or the sum of the
frequencies) is taken as 1,000 (for we are converting the
‘
observed frequencies into “ per-milles’’). We take the sum-
mational curve figure and then take one-half of the total
vertical scale (or 500) on a pair of dividers and, with this,
measure off the distances aa', bb', cc', etc., along the vertical
scale lines and from the points where the latter intersect the
summational curve. Thus we get the points a', b',c',d', e',
and then (with a “french curve”) we draw a smooth curve
through them.
Next, with a pair of dividers, we find the shortest distance,
measured along some horizontal scale line, between the curve
a', b', c',d', e' and the summational one. Perhaps there are
several scale lines all sensibly the same in length and then we
approximate by finding the middle one. The places are
marked where this shortest horizontal line cuts both curves :
they are g and! m Fig. 6. From g and /' perpendiculars are
69
Fic. 6.
70
dropped to cut the horizontal axis, and these latter points,
read off on the scale of lengths, give the abscissae of the shortest
half-range : the latter is about 18-5 to 21-5 cms., and within
this range of lengths one-half of all the fish in the catch are
contained.
We now go further. From the point g'', on the vertical
scale, 150 units are measured downwards getting the point h''.
A horizontal line h'' h is drawn to cut the summational curve
in h and a perpendicular hh' is drawn to cut the horizontal
axisinh'. Between g' and h', that is, between about 21-5 and
23 cms., another 15 per cent. of all the catch is contained.
Next we prolong the vertical line, f'' f', upwards to cut the
summational curve in f, and then a horizontal ff''' is drawn
across to cut the vertical axis in f'''. From the latter point
150 units are measured upwards on the vertical axis giving a
point on the latter at about 1,000. Therefore a further 15 per
cent. of the fish are contained within the range of lengths
14 and 19 cms.
Summarising we find :
One-half of all the fish are over 19 and less than
22 cms. in length ;
80 per cent. of all are greater than 14 and less than
23°D cms. in length.
Obviously we can extend the method. We might repeat
the above construction, using two-thirds of the vertical scale
length, or three-fourths: these figures would give us the
shortest two-third and three-fourths’ ranges. Or we may take
the point 20 cms. on the horizontal scale, draw a perpendicular
upwards to cut the curve and then a horizontal across to cut
the vertical axis in the point 600. That shows that 60 per
cent. of all the fish are 20 cms., or more than 20 ems. in length.
Or, again, we may find the mode and then draw a horizontal
across to cut the vertical axis. Stepping off 25 per cent. cf
the latter scale on either side we get two additional points.
(i
From them horizontals are drawn to cut the curve, and from
the points of intersection perpendiculars are drawn to cut the
horizontal axis. The latter points are the two quartiles.
It must be noted that the degree of accuracy of such
determinations of the modes, points of inflexion, or measures
of dispersion depends upon good draughtsmanship. This is
not difficult to attain. There will be some personal differences
in the results,* but we submit that these are usually smaller
than any differences that ought to affect the conclusions that are
to be made. These conclusions are to have certain probabili-
ties: for instance, we lay it down that it is to be 2 to 1 that
the fish caught on a certain area, in a certain month, and with
a 6-inch mesh trawl-net, are (say) between m and m cms. in
length. Then we find n and m, or we wish to find what fraction
of the whole catch of fish are between n and m cms. long in the
same area and in the same circumstances. Then n and m
being postulated we find the corresponding probability.
Extensions will readily suggest themselves.
CHARACTERISTIC LENGTHS OF THE PLAICE Caucut DuRING
THE PRE-WaR PERIOD, 1908-1913.
We now give a series of tables, 3 to 13, which summarise
the results of the trawling experiments made during the six
years 1908-1913. These data are intended as a record of the
condition of the plaice population on the eastern side of the
Trish Sea during the years immediately preceding the war, and
they will enable us to make a comparison with the condition
* Analytical methods can always be employed to find the mode (dy/dx a
maximum on the summational curve), and the points of inflexion (dy2/d22
maximal and changing sign on the summational curve). We think such
treatment would be pedantic. Measures of dispersion must be approximate
so long as we do not know the equation to the frequency curve.
72
that followed the partial cessation of fishing which occurred
during the vears 1914-1918.
The arrangement of the data is as follows :—
Tables 3 to 10 record the lengths of plaice caught in a
trawl-net of 6-inch mesh, throughout the year, on the regions
Luce Bay, Morecambe Bay, etc., Blackpool to Liverpool Bar,
Mersey Estuary, Beaumaris and Red Wharf Bays, etc.,
Carnarvon Bay and Cardigan Bay. The actual frequencies of
occurrence of each one-cm. group and the frequencies per
thousand are given.
Table 11 gives the same kind of data for plaice caught
off the Mersey Estuary in a shrimp trawl-net of 2-inch mesh.
Table 12 gives the same data for a number of hauls made
with trawl-nets of 4-inch, 6-inch, and 7-inch meshes on the same
grounds and at about the same times.
Table 13 gives the dispersions, calculated by the methods
indicated in the previous section of this report, for the distribu-
tions of Tables 3 to 12.
73
Table lil. Luce Bay, Sept.-Dec., 1908-1912.
el
Ct Ov St Ot
bok —
SOP WNWHOODAATE WN HOOD
wWwHwwwwwowrmbpdbddywerrprth
AAAAaannnargana ana dc
|
Mean
if bad es length if flee
2 0-2 37°5 173 22:3
6 0:8 38-5 155 20-0
7 0-9 39-5 119 15-4
9 1-2 40:5 91 11-7
22 2-8 41-5 58 75
79 10-1 42-5 66 8-5
271 34:8 43-5 42 5-4
372 48-0 44-5 51 6:6
412 53-2 45:5 18 2:3
523 67-5 46-5 PAT 3-5
538 69-5 47:5 17 2-2
454 58-6 48-5 13 1:7
412 53-2 49-5 12 1:5
380 49-1 50-5 5 0-6
306 39:5 51-5 6 0:8
290 37-4 52-5 3 0-4
292 37:7 53:5 6 0:8
257 33:2 54-5 2 0-2
231 29-8 55-5 oars eis
259 33:4 56-5 2 0-2
239 30:8 57-5 1 0-1
218 28-1 58:5 3 0-4
276 35-6 59-5 aoe
299 38:6 60-5
264. 34-1 61-5 ae fis
251 32-4 62-5 D2 0-2
207 2 —
Motals#sceeee 7,748 999-6
74
Table 1V. Morecambe Bay, &c., 1908-1913.
Estuary
MORECAMBE Bay. OF THE
Duppon.
June. July. | August. | March—May.
fo eiales fem lea) of. ~\it coe 1 maka ee
10-5 Bee Bae Beedle oe ES i
11-5 e. Mee rl ee i no igi tes
12-5 Tea its Pease es | Ae Pe aie is ane
13-5 Se awilt eek oe | 1] 0-9 1 | 0-7 23 | 6:3
14-5 9 3°8 | 3 2:6 5) || 3:3 82 | 38-2
15-5 39 16-6 36 31-1 | 2) 13-7 205 75:3
16:5 78 33:3 15: | 64-9 | 69 | 45:1 302 +°100-6
17-5 171 729 | 135 116-8 101 66-0 390 117-2
18-5 302 128-8 101 87-4 116 75:8 482 | 118-8
19-5 305 130-1 | 147 | 127-2 128 | 83:7 413 111-1
20-5 416 177-4 | 180 155-7 | 141 | 92-2 315 | 97-6
21-5 345 147-1; lll | 96-0 NB || 89-5 221 | 81-9
22-5 303 129-2 113 | 97-7 178 116:3 | 170 | 66-2
23:5 183 78:0 65 | 56-2 157 102-6 178 | 51-7
24-5 90 38-4 7 61-4 151 98-7 102 39-2
25-5 50 21:3 42 | 36:3 123 80-4 84 | 29-0
26-5 23 9-8 ay) 27:7 74 48-4 68 | 20-9
27-5 18 7:7 18 15-6 | 67 43°8 44 14-6
28-5 5 2-1 10 8-7 30 19-6 43 10-5
29-5 33 1:3 7 6-1 16 10-5 32 6-9
30-5 2 0:9 | 4 3°4 9 | 5:9 27 | 4-6
31-5 1 0-4 | Seb WI eee nl 1-9 8 3-0
32°5 1 0-4 i 0:8 | 2, 1:3 4 | 1:9
33°5 I 0-4 3 | 2:6 a 0:7 4 1-2
34:5 a re |) aes nae doe” Il Paes 4 0-7
35-5 ESA lh 3-- i 0-8 | Ie
2,345 | 999-9 1,156 999-9 | 1,530 | 1000-1 | 3,223 997-4.
* Calculated frequency curve.
70
Table V. Blackpool to Liverpool Bar. 1908-1913.
=; =e Te = we ae are ar es youw
June. | July August. September. October.
|
i | Hi hes | f | f hee if | if ates f | f rien f if Ses
11-5 a ae 1 1 eee eee eee | '
12-5 a Ds eae 6 | ; 1129 Reena 1 0-4
13-5 1 0-5 1 Be DAN ae 9 39; 10; 40
14-5 12 6-4 8 ee 57 | 3:8 34 12-1 19) Gad
15-5 39 20-7 30 | 4:8) 131} 24-3) 111 31-9 75 | 30:3
16-5 106 56-2 | 129| 29-7] 267| 55:9] 269 57-7 | 201 | 81:3
17-5 205 | 108-8} 320 85-4 | 473 | 89-4 | 459 82:9 | 231 | 93-4
18-5 304 | 161-3 601 | 139-3 | 740| 106-0] 517] 101-7 | 250] 161-1
19-5 263 | 139-5 | 838 | 162-9 | 794] 114:0| 542| 111-2 | 196| 79:3
20-5 231 | 122-6] 676 | 154-2] 839] 111-5 | 557} 111-3] 167 | 67:5
21-5 228 | 121-0] 495 | 127-7/ 681] 101-8/ 506] 1036 | 152] 61-5
22-5 183 97-1| 433 | 93-0] 57h | 882] 449/ 91-2] 160) 64:7
23-5 124 65-8 | 320 69-4 | 444) 73:3] 339) 76:3] 164) 66:3
24-5 67 35-5 | 254 47-9 | 338; 589] 311 Ci Vig | STG
25-5 45 23-9 | 159 32:3 | 262) 460] 245 47-1 | 156) 63-1
26-5 24 12-7 83 21-5 | 231 “35:2: 176 85-1 | 140) 56-6
27-5 20 10-6 63 14-1 | 182)|, 926-4) 798 25-4 | 122 | ~49:3
28-5 9 4-8 25 93 | 146 19-4 88 17-8 97 | 39-2
29-5 14 7-4 22 6-1 86s «14 54 12-1 61 | 24:7
30-5 5 2-7 6 4-0 63 10-0 34 8-1 37 | 150
31-5 3 1-6 14 2-8 36 | 7-1 18 5-2 22 8-9
32-5 2 1-1 15 18 34. | 5-0 18 3:3 8 3:2
33-5 x 5 OE fee eA 3-5 4 20) ll 4-4
34-5, an 6 0-8 | 21 | 2-4 6 13 | 5 2-0
35-5 es 0-5 123) 1-6 5 0-7 | 4 1-6
36-5 ile 0-4 Wed 1-1 6 04) 2 0:8
37-5 3 0-3 3 | 0:8 1 O22 0:8
38-5 h 2)] 0:28 |=. 0-5 1 O-1 | 1 0-4
39-5 ses (Pt Ae ene | O:3) he io: Eta | a
40-5 Te 0-2 1 0-4
41-5 1 | 0-2 | 0-4
1,885 | 1000-2 |4,516 | 1009-6 |6,492 | 1000-9 | 4,889 | 1003-7 | 2,473 999-9
* Calculated frequency curves.
76
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(et
Table VII. Beaumaris Bay, Red Wharf Bay, &c. 1908-1913.
January. June. July. August.
Mean
length. a a
ui UPTO i | Rie f Flo i Foo
12:5 ae Sac Sco 2 1:0 2 1-0
13-5 4 2-9 2 0-9 1 0-5 3 1:5
14:5 9 6-7 3 1:5 3 | 1-6 3 1-5
15-5 28 20-7 32 15:8 26 | 14-3 12 5-9
16-5 43 32-1 92 45:3 43 23-7 5] 28:3
17-5 63 47-0 213 104-9 124 68-4 145 Tlsg)
18-5 81 60-4 261 128-5 207 114-0 231 114-6
19-5 91 67-9 259 127-6 273 150°3 318 157-7
20-5 70 52-2 237 116-8 255 140-4 282 139-8
21-5 82 61-2 153 75-4 216 Ie 260 129-0
22-5 85 63-4 113 55:7 156 85-9 170 84:3
23-5 69 51:5 77 37:9 113 62-2 127 63-0
24-5 60 44-8 75 36-9 86 47°3 105 52-1
25:5 69 51:5 64 31-5 65 35°8 67 33-2
26-5 78 58-2 47 23-1 42 23-1 50 24:8
27-5 84 62-7 52 25-6 37 20-4 37 18:3
28-5 67 50-0 56 27-6 36 19-8 34 16-9
29-5 67 50-0 47 23°1 31 13-5 29 14-4
30-5 68 50-7 44 21-7 23 12-1 26 12-9
31-5 62 46:3 45 22-2 17 9-3 20 9-9
32:5 44 32:8 56 27-6 18 99 15 7-4
33-5 28 20-9 37 18-2 14 Wey 7 35
34:5 34 25-4 19 9-4 7 38 6 2-9
35-5 14 10-4 16 1-9 8 4-4 1 0-5
36-5 16 Lg 8 39 5 2-7 3 1-5
37-5 2 1-5 6 2-9 2 1-0 2 1-0
38-5 4 29 5 2-4 6 3-2 2 1-0
39-5 i) 3-7 6 2-9 Be abe 1 0-5
40-5 3 | 2-2 5 2-4 os aR 1 0-5
41-5 2 1-4 ot O00 1 1-0 aon 308
42:5 1 0-7 ' a : ;
43-5 1 0-7 : 60 ee
44-5 1 0-7 5
45:5 2 1-4
46-5 1 0-7 |
47-5 1 0-7
48-5 1 0-7
1,340 | 998-9 | 2,030 999-6 | 1,817 996-4 | 2,016 | 999-8
78
Table VIII. Beaumaris Bay, Red Wharf Bay, &c. 1908-1913.
September. October. November. | December.
Mean |
length. | ———}-—, —t- — -_ ——— aa
PME eae
11-5 3 0:6 26 see a a as
12°5 8 1-6 3 0:3 oot 1 0-4
13-5 20 3-9 14 1:5 5 | 0:8 2 0-8
14:5 68 13:3 76 8-7 29 4-9 10 4-0
155 | 158 31-0 421 48-4 146 | 24-5 20 7-9
16-5 291 57-0 | 1,197 137-9 350 58:8 66 26-1
17-5 438 85:8 | 1,493 In 7fler/ 413 69-4 94 37:2
18:5 396 77-6 | 1,155 132-2 360 60-5 158 62-5
195 | 430 84:3 802 92-3 343 57-6 175 69-2
20° | 392 76:8 579 66-6 341 57:3 218 86:3
21-5 319 57-0 502 57-7 362 60-8 201 80:5
22:5 342 67-0 405 46-6 345 58-0 224 88-6
23-5 | 296 57-9 310 35-6 339 56-9 211 83-5
24-5 337 66-0 268 30:8 363 61-0 162 64-1
25:5 299 58-6 261 30-0 349 58°6 154 60-9
26-5 286 56-0 275 31-6 336 56-4 152 60-1
27:5 278 54-4 219 25:2 312 52-4 Unven | 46:3
28-5 217 42-5 215 24-7 361 60-6 120 47-5
29-5 153 29-9 161 18-5 341 57-3 81 32-1
30-5 131 25-6 107 12:3 272 45-9 109 43-1
31-5 85 16-6 81 9-2 176 29-6 68 26-9
32-5 59 11-6 52 5-9 137 23-0 59 23°3
33-5 37 73 39 4-5 73 12:3 29 11-5
34:5 22 4:3 22 2-5 60 10-1 28 |
35-5 17 3°3 12 1-4 38 6-4 15 5-9
36-5 7 1-4 12 1-4 30 5-0 12 4:7
37-5 7 1-4 4 0-5 14 2-3 8 3-2
38-5 3 0-6 4 0-5 8 esha 12 4-7
39-5 1 0-2 2 0-2 14 2:3 10 4-0
40-5 4 0-8 1 0-1 14 2-3 6 2-4
41:5 es ae 3 0:3 6 1-0 + 1-6
42-5 : : 50 aes 2 | 0:3 1 0-4
43-5 2 0-2 1 0-1 ee of
44-5 oe 2 0-2 Sa eee
45:5 20¢ 4 0-4
46-5 1 0-1 1 0-1
47-5 Oe
5,104 | 994-3 | 8,697 | 999-4 | 5,950 | 999-9 | 2,527 | 1000-8
79
Table IX. Carnarvon Bay. 1908-1913.
June. July. August. September. October.
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*‘panuyjuoo— |X WqeL
85
Prevalent Lengths of Plaice on the Various Grounds.
There is no need to consider the data of these tables in
the present place—they are intended as a permanent record
and can be used in many conceivable ways. Here we only
point out some of the more obvious characters of the fish taken
on the regions investigated.
Luce Bay.
One-half of all the plaice taken were over 21 and under
34 cms. in length and another 15 per cent. were over 34 cms.
and under 40-5 cms. These are the biggest fish taken in any
inshore area on the eastern side of the Irish Sea. Why ?
It is to be noted that observations were only made during
the months of September to December. The hauls were made
with the object of getting spawning fish for the hatcheries at
Port Erin and Piel, and the Bay was fished by permission of the
Fishery Board for Scotland. As we have no records for the
other months it is impossible to say whether or not there is
any marked seasonal variation.
The Bay is well protected from 8.W. to N.W. winds, and
' this may be a condition of importance. But we think that
the reason why there are bigger plaice in Luce Bay than else-
where in the district studied is mainly that the region is closed
against trawling by al] kinds of vessels. Only a small amount
of fishing, by means of gill-nets, goes on, and the plaice are
protected. Luce Bay is a closed area, and it is interesting on
that account.
The New Quay Grounds in Cardigan Bay.
Inside the three-miles’ limit, and extending to the N.E.
for several miles along the coast of Cardigan Bay, are the
New Quay grounds. Here also are relatively large plaice
during the early months of the year. They are not so abundant
86
as in Luce Bay, for trawling by sailing vessels is permitted.
The shortest half-range is from 25 to 34 cms., and 65 per cent.
of all the fish caught were over 25 and under 39 cms.
Beaumaris and Red Wharf Bays.
This also is an inshore fishery, mostly inside the three-
miles’ limit. The main season is in the late autumn—about
October to January. We shall show later that this autumn
fishery depends on a migration taking plaice from the regions
to the N.E. The fish are bigger than on the other grounds in
Liverpool Bay and off the Lancashire coasts, the half-range
being from 19 to 28 ems.
Carnarvon Bay, Mersey Estuary, Liverpool Bar
to Blackpool, Morecambe Bay (inshore).
All this area may be regarded as a single, natura] one.
The fishery is carried on mainly by half-decked vessels, a few
smacks, and an occasional steam trawler. It is mostly inside
the three-miles’ limit, though there is also a considerable area ~
of plaice-ground outside this contour. The main fishing season
is from ahout July to October. The whole ground may be
regarded as a typical small-plaice one.
The characteristic lengths of the plaice caught in the
months August to October are :
Carnarvon Bay ... ... 18 to 24 cms.
Liverpool to Blackpool ... 18 to 22 ems.
Mersey Hstuary... ... 20 to 24 cms.
Morecambe Bay _... ... 20 to 25 cms.
These are the shortest half-ranges, comprising 50 per cent.
of all the fish caught.
87
There is a fairly well-marked seasonal variation in length.
Thus, taking the Mersey Estuary, we get :
May ... oF oe +. 18-21 cms.
June... aN a ... 17-20 cms.
sullivan ie es ee ... 18-21 cms.
August ... vies oe ... 20-24 cms.
These are also the shortest half-ranges. The differences
are due to the natural growth of the plaice and also to successive
waves of migration of small fish from the more crowded, very
shallow waters, to the sea just offshore. This we refer to in
the section dealing with migrations.
The Nursery Grounds.
These we refer to when dealing with the life history of the
plaice in the Irish Sea.
88
PART Al:
THe Lire-HIstory OF THE PLAICE.
We next consider the available knowledge as to the life-
history of the plaice on the eastern shores of the Irish Sea.
There is, of course, much that has still to be investigated with
respect to this: the embryology, the possible existence of
local races, and the possible spawning-grounds in St. George’s
Channel and the Welsh Bays. The information that is at our
disposal, however, enables us to make such a general picture
of the life-history as may be of use to the administrators.
The Spawning.
Plaice eggs are found in the plankton collected almost
everywhere offshore, between the Solway and Cardigan Bay,
in the months of February, March, and April. Exceptionally
the eggs have been found in January as the result, we think,
of the spawning of fish well to the southward in St. George’s
Channel. Spawning occurs in the pond at the Port Erm
Hatchery during the months of March, April, and exceptionally
in May. ‘The fish kept in the tanks at Piel, Barrow-in-Furness,
spawn a little later, usually about the end of March, in April,
and in May. April is the best month for the fish in the tanks,
but in the open sea March is perhaps the best month. There
is, of course, much variation, from year to year, in the time
of spawning, and this is to be associated mainly with the
temperature of the sea at the time of spawning and during the
previous months, when the reproductive organs are most
rapidly developing. It also depends on feeding, as is shown
by our experience in the hatcheries, where the fish must be well
fed if the roes are to develop fully. A close study of the
variations in the temperature of the water (both in the tanks
and in the sea) and in the abundance of the eggs found would
89
be most interesting, but this calls for very exhaustive experi-
mental and observational work.
We think there are two sources of the plaice eggs that are
found in the plankton of the Irish Sea: (1) somewhere to the
S.W. in St. George’s Channel, and (2) the grounds near the
entrance to the Solway Firth. The reason for attributing by
far the larger share of plaice eggs to the St. George’s Channel
grounds is the direction of the tidal streams in this area and
in the Irish Sea. The flood-stream sets in a northerly direction
in St. George’s Channel, with indraughts into Cardigan and
Carnarvon Bays. It clings strongly to the Anglesey promon-
tory and then sets towards the East, round into the Liverpool
Bay area. Near a line crossing the Irish Sea from Morecambe
Bay to about Ramsey the northerly flowing flood-stream
slackens, and there is a general tendency for the drift of
wreckage and other floating objects to be arrested on the
North Lancashire and Cumberland coasts, between Morecambe
Bay and about Drigg, in Cumberland. The ebb-stream runs
in nearly the opposite directions, but there is also a general
tendency to a drift from South to North, so that more water
enters the Irish Sea with the flood-tide from the South than
leaves it with the ebb-tide. Approximately the whole contents
of St. George’s Channel and the Ivish Sea are changed every
year, the water flowing out through the North Channel and
entering by the South.
Plaice eggs spawned in St. George’s Channel will, therefore,
tend to drift slowly to the North and East, round Anglesey,
into the shallow-water region between the North Coast of
Wales and the “ head of the tide,’ between Morecambe Bay
and Ramsey, in Isle of Man.
Such a southerly spawning area is thus to be deduced from
a knowledge of the effect of the tidal streams, but it has yet to
be actually observed. The existence of northerly spawning
crounds has long been asserted by the trawlers. It is said
90
that plaice spawn just offshore from Peel, in Isle of Man, and
in the entrance to the Solway Firth. In 1920 we were able to
investigate the latter ground. During the months January
to April the Lancashire and Western Sea-Fisheries Committee
allowed us the partial use of the s.s. “‘ James Fletcher,’ and
about thirty hauls were made on the region between Ramsey
Bay, in Isle of Man, and the entrance to the Solway Firth ;
100 drift-bottles were set free, and 367 plaice were marked
and liberated. The results of these investigations enable us
to describe the northerly spawning ground under the conditions
of 1921.
It lies about eight miles to the west of St. Bees’ Head, in
Cumberland, extending North and South for about eight to
nine miles. Its bearings are:
Centre, 7 miles W. by S. from St. Bees’ Head.
Northern end, 9’ N.W. from St. Bees’ Head.
Southern end, 9’ W. by 8. from St. Bees’ Head.
Its depth varies from 15 to 20 fathoms. It is situated in nearly
the coldest part of the Irish Sea (during February and March).
There are several banks off the N.E. of Isle of Man (“‘ Bahama,”
“ King William,” and the “Shoals”’). Between these banks
and the fishing ground in the entrance to the Solway, called
the ‘‘ Slaughter,” there is an interchange of plaice, such that
the bigger fish tend to migrate from the “Shoals,” about
February, over to the “ Slaughter,’ where they spawn. The
spent fish then disperse, many of them returning to the Shoals’
area and to the South-west.
In February of 1921 mature plaice were found between the
“Shoals” and the spawning ground. In March they were
found in greatest abundance on the spawning ground, and at
the middle of April no mature fish at all were found there, but
spent plaice were then to be taken on the “Shoals.” About
March 21st the spawning season culminated, and by April it
was practically over.
ol
The numbers of mature female plaice caught per hour’s
- trawling* were as follows :—
On the “ Shoals ”
On the “ Slaughter ”’
On the southern part of the “‘ Slaughter ”’ :
3-0; April, 6-3.
South from the “ Slaughter ”’
: in February, 8:5; March, 5-2; April, 7-9.
: in February, 8:9; March, 9-4.
in February, 4:8; March,
: in February, 5-9; April, 2-2.
The proportions of the female fish taken in the mature
condition on the various grounds were as follows :—
(1) On the “Shoals”: February, 16 %; March, 31%; April, 64 %.
(2) On the “Slaughter”: February, 86 %; March, 81%; April, 37 %.
The sizes and ages of the fish dissected on board the
vessel are given in the three following tables—which are of
much interest :—
Sizes and Ages of the Female Plaice Examined.
Length (ems.). | IV V VI Wa |) \WAGHE || “1D-¢ x EXOT | eNCHT
ZO-DO NM sacisecseniee: 1
S335) ceananaaooo 2 1
BO=4 0 Mseeceses: 7 U 7
CM dN5). scncnaougae 1 6 9 3 2
AG=DO) Weecrseeies 5 3
ein eeeee eee 2 1 1 1 2
BO60) fc -5.: |
(NIEHS) Gonsoneso0 1
Sizes and Lengths of the Male Fish Examined.
Lengths (cms.). III IV V VI
PREY soncdooscabopsaecoonpoor 1 1
Ble318) cocomocposasbnocqc0a00Ge 1
S150) Soonnonocasuencebdoadne 2 | 6 1
* By an otter trawl-net of about 40 feet in spread.
92
Percentages of Mature Female Plaice at Various Sizes.
Immature. Mature. | Percentage of
| Mature.
2530) cle. aaee 73 Pee | san
DLedO ae wsccesesacesscestassecel| 25 ee. 47 65 3 —
3O=40 Hoc wnswesarcwmecnactiaeee 3 92 | 96-8
TTC ees eens ers, it 45 | 978
|
In general, female plaice were observed to be mature at
about 33 cms. in length and at about Age-group IV. (IV, V,
etc., mean over 4 years and under 5, over 5 and under 6, etc.)
At the same time that these hauls were made a number
(100) of surface drift-bottles were set free, the object being to
ascertain in what directions the plaice eggs spawned on the
“Slaughter ”’ grounds would be carried during the period when
they, and the larvae hatching out, would be pelagic in habit.
About half of these drifters were ultimately recovered and all
of them were picked up along the South Coast of Scotland.
This is what is to be expected, because the prevailing
winds during the late winter and spring are from the
South to West in this region. There were also some Hast to
North winds, and these might have been expected to carry
the bottles down towards the coasts of Isle of Man and
Lancashire, but this was not the case. The tidal streams
in the Irish Sea, North of the Ime joming Ramsey and
Morecambe Bays, set in and out through the North Channel
(between Mull of Galloway and the Antrim coast) and then
North and South between Isle of Man and the Cumberland
coast. Further, we see that there is a gradual, resultant drift
of water, from the sea off the Lancashire coasts, up through
between Isle of Man and Cumberland and then out through
the North Channel. Therefore an unusual spell of North to
East winds might, indeed, drive the drifters down to the
93
South of the “head of the tide,’ but, on the backing of the
wind again to West and South, they would be carried back
again into the Solway and South Scottish coast.
It is reasonable to conclude, therefore, that plaice eges
spawned on the Solway “Slaughter” ground will be carried
mostly into the Solway Firth and into Wigton and Luce Bays
(on the Scottish coast). The shallow water grounds here are
pre-eminently “ small plaice ”
as great an extent as are those off the Lancashire and Cheshire
coasts (see the tables, “Solway Firth”). The northern part
of the Irish Sea is therefore supplied with small plaice, which
grounds, or nurseries, to at least
are spawned and reared in the same sea region.
Hatching and Transformation Stages.
The plaice eggs found in the tow-nets are, from our
experience, always fertilised. Now an unfertilised plaice egg
will generally remain alive and buoyant, floating at the surface
of ordinary sea-water for about a week. If they were present
in notable numbers in the plankton they would certainly have
been observed, but there is no doubt that such unfertilised
plaice ova are very rare. It is fairly certain, then, that there
is definite pairing in the sea, or at least that ripe males and
females come together in the same local shoals, at the time of
spawning. Thus we account for the absence of unfertilised eggs.
The period of incubation varies from about three weeks,
at the beginning of the hatching time, to about ten days, in
April. The sea-temperature in the region between Morecambe
Bay Light Vessel and the Lancashire coast rises about 4° C.
(from 5° C. to about 9°C.) during the period Ist March to
30th April. But the differences are considerable in the various
regions: thus the temperature at lst March may be one or
two degrees lower at the Solway Light Vessel and at least a
degree higher at Carnarvon Bay Light Vessel. There are also
considerable differences from year to year, and there are minor
94
differences even at places a few miles apart, at the same time,
these latter variations being due to cold water ebbing back
from the land (which is always colder at this time of year than
is the sea). We cannot say, precisely, how Jong it takes a
plaice egg to incubate in the Irish Sea because of all the above
variations. The plaice at Port Erin Hatchery always spawn
several weeks earlier than they do at Piel, in the Barrow
Channel because of the higher sea (and land) temperature at
the former station. There is a rather well-marked mathematical
relation between the temperature and the incubation period
of a fish egg: the higher the temperature, the shorter the
incubation period. So far, however, we have not made
experiments stating this relation exactly in the case of Irish
Sea plaice.
Neither has the time required for the later development
been made out, though it is known that the baby plaice in the
Port Eri spawning ponds have usually become transformed
by the end of April. The fish hatches out from the egg as a
larva, carrying a large yolk sac, and in the course of about
two weeks this organ becomes very small, and then, later on,
quite disappears. About the time of its disappearance the
transformation (or metamorphosis) occurs; the body begins
to flatten from side to side, and the left eye begins to show
on the right-hand side of the head, because of the twisting
(from left to right) of the bone between the mouth and the
brain-case. In about a month from the date of hatching the
metamorphosis has been completed and the fish is become
definitely flat. At all stages between the egg and the fully-
transformed larva, however, the latter can be identified as a
young plaice, though it is very like the flounder and dab.
The First Shore Stages.
At about the end of May and the beginning of June,
according to the nature of the season, the young plaice first
95
‘
come on to the shore as
be seen in the shallow shore-pools left by the receding tide.
They are very active, but can easily be caught. They must
be present on the shores of Cheshire, Lancashire, and Cumber-
‘sixpenny flukes.” They can then
land at this time of year in enormous numbers. The mortality
must also be very great at this stage, for the little, shallow
shore-pools are apt to dry out as the tide recedes, or soaks into
the sand, and when the sun is hot the larvae must perish. No
precise observations have been made enabling us to state the
time when the transformed larvae first come shorewards, and
in what relative abundance ; but undoubtedly both conditions
vary from year to year. It is certain, however, that it is
nearly always about the same time (the very end of May)
when the plaice first come on to the Lancashire shores, and it
is probable that this is so even though there may be bigger
differences, from year to year, in the dates of spawning and
hatching. It is very likely that a certain combination of
conditions (sea-temperature, sunlight, food) must be present
in order to enable the baby fish to survive when they abandon
their drifting, pelagic life, go to the bottom and seek the very
shallow-water grounds close inshore.
Food of the Larvae and Transformed Plaice.
In general, the larvae first feed on algal spores (but this
remark applies to observations made on the larvae hatched
out and transformed in the Port Erin ponds). Later on they
feed almost entirely on Copepods (Harpactids chiefly) though
other organisms are, of course, eaten. A full report on the
food of the larval plaice collected from the spawning ponds
and from the shore has been prepared by Mr. Andrew Scott
and will appear in a forthcoming part of the Journal of the
Marine Biological Association.
96
Growth of Plaice during the First Year.
This we were able to make out by measurements of little
plaice reared in the Port Erin tanks. The results are as
follows :—
31-40 mm., 1; 61- 70 mm., 8
41-50 ,, 3; (12 O0 ee 0
D1-60 0 eaele 81-00" Tea
91-100 d
Thus, there is considerable variation between individual
fish as one might expect. This variation continues, and even
becomes greater in subsequent stages of the life-history. In
1921 we made collections* of young plaice (and other flat
fishes) in the shallow bays in Isle of Man, and on the Lancashire
and Cheshire coasts. In May, the length varied from 13 to
50 mm. in the case of the Manx fish. From now onwards the
plaice grow rapidly, increasing in length about six or seven-fold
by the end of the autumn. Precise measurements (averages)
for Cheshire shore plaice are as follows :—
June, 42-2 mm. ; July, 46-5 mm. ;
Aug., 52:5 mm. ; Sept. 58-6 mm. ;
Oct., 67-4 mm. ; Nov., 65-5 mm. ;
Dec., 61:1 mm. ; Jan., 662 mm.
These are all first-year plaice, for each was examined by
inspection of the otoliths (or earstones). The latter are, of
course, very small, but it can easily be seen that they consist
‘
only of the central, opaque “nucleus.” Towards the end of
the year this central white spot becomes surrounded by a semi-
transparent ring, and thereafter an opaque white ring is formed
during each summer and autumn, and a semi-transparent ring
during each winter and spring. (Chemical tests showed that
* The ordinary haul “ push-net”’ used by shrimpers in Lancashire was
employed. The collector wades in water of about 2-feet depth and pushes
the net in front of him. The fish can often be seen. The method is a very
admirable one for the collecting of small shore fishes on a shallow, sandy
coast.
oT
the substance of the otoliths was made up of the modification
of calcium carbonate, known as aragonite. It contains about
98 per cent of CaCOs;, the remainder being organic matter and
water. )
During June the “ sixpenny flukes ” leave their foreshore
and very shallow-water habitat and migrate further out to sea.
In July and onwards they can be taken in the shrimp trawl-nets,
and their abundance there has been, for a long time, the
interesting feature in the life-history of the plaice from the
point of view of fishery regulation. A great deal of attention
has been devoted to this question in Lancashire: whether or
not shrimp-trawling does more harm to the general fishing
industry than it is worth? From the beginning of their
period of control the Lancashire Sea-Fisheries Committee made
many observations on the relative abundance of plaice and other
fishes in the catches made by the shrimp-trawlers in their
district. The late Superintendent, R. A. Dawson, devised a
special form of the shank-net, designed to permit the capture
of shrimps while allowing young, flat fishes to escape, but this
instrument never became adopted. In 1899 the Committee
applied to the Board of Trade (which was then the Central
Fishery Authority in England) for confirmation of a By-law
restricting trawling by fine-meshed nets in the important
nursery ground off the estuary of the Mersey, but this measure
was very seriously opposed by the local fishermen, and the
Board refused to sanction it. Since then the question has not
been raised again.
Table 11, gives a summary of the results of the measure-
ments of plaice made in the experimental hauls carried
out by the officers of the Committee on the Mersey grounds
during the period 1908-1913, and there is a detailed report on
a series of observations made by Capt. + Kecles during the years
1899-1920, which gives a very fair idea of the conditions on
this nursery ground. First, as to the sizes of the plaice taken :
G
98
this varies, of course, according to the time of year. During
the wimter months, November-March, the fish are smallest,
because then they belong mostly to those hatched in the
previous year. The prevalent length is about 7 ems. (2? ins.),
and 50 per cent. of all are between 6 cms. and 8 ems. in length
(25 ins. to 34 ins.). During the months May to July there are
three maximal lengths, or prevalent sizes: about 5 cms.
(2 ins.), 9-5 cms. (32 ins.), and about 14 cms. (53 ins.). That
means that a great number of the plaice caught in May to
July are those that have been hatched in the same year (they
are two to four months old). Then there are plaice that are
one and two years older (that is, about 14 and 2+ years old).
It is impossible to be more precise as to the ages of fish caught
in the shrimp-trawl (on pp. 131-2 we discuss the general
question of the growth rate of the fish), but the following
results are useful: half of all the plaice caught during May to
July are from 11} to 163 ems. long (that is, 44 to 63 ins.), and
half of all those taken durmg the months August to October
are from 11 to 16 cms. long (that is, 44 to 62 ins.). This will
give a good idea of the kinds of plaice caught in the course
of shrimp-trawling.
Next, as to the numbers caught. A summary of the results
of the Mersey experimental hauls is given by R. J. Daniel,*
and this shows the actual numbers per haul, per hour’s fishing,
etc., taken between 1898 and 1920. The number per haul
varies between 14,697 (in 13 hour’s drag) and 0. The average
number per hour’s fishing per annum varies between 1,197
(in 1911) and 64 (1904 and 1916). There is a very evident
periodicity in abundance of young plaice on this ground, and
to this question we return Jater in the report (p. 136).
The short statement made here will show, however, what an
extremely heavy toll shrimp-trawling makes on the plaice
population of the inshore nursery grounds in the Irish Sea.
* Ann. Rept. Lancashire Sea-Fish Lab. for 1919 pp. 51-71.
99
Whether that amount of destruction of small fish is a thing to
be restricted or prevented is not so easy a question to answer
as it appears to be at first sight. To that again, we return in
a later section of this report (see p. 167).
The Nursery Grounds and their Conditions.
These extensive shallow-water nursery grounds are of
extreme importance to the fisheries, and it may well be the
case that the attention of future fishery authorities will be
directed to them far more than to the offshore regions, which
at present almost monopolise investigation. From the natural
history point of view they are of surpassing interest, and we
feel that far too little research goes on here. They are by far
’ zone of the sea, and that is, of course,
b)
the most “ productive
the reason why they are fish nurseries. The conditions that
make them productive are: (1) The drainage from the land
carrying fresh water which brmgs down enormous quantities
of organic substance, in solution or as a sediment (all of this
is utilised by living organisms); (2) The low salinity of the
water; (3) The relatively high temperature, and (4) The
greater degree of sunlight. The sand everywhere contains
abundant vegetable life in the form of Diatoms, Flagellates,
and Dinoflagellates (microscopic plants and ** plant-animals ”’),
and one can, nearly everywhere, see this as a yellow-brown or
greenish scum on the surface of the sand. Beneath the surface
the sand is, nearly everywhere, blackish in colour as the result
of the action of sulphuretted hydrogen produced by the
decomposition of dead organic substance. In the surface layers
of the sand and in the water just over that layer there are
numerous Copepods and small worms. Nearly everywhere
there are very numerous shellfish—cockles, small mussels,
Mactra, Scrobicularia, Nucula, etc. A minute fragment of
zoophyte may contain dozens of small mussels about the size
of a very small pinhead, and on some suitable bottoms the
100
zoophytes and polyzoa growing there may appear as if they
were thickly dusted over with such minute mussels. Some
counts made recently showed that extensive areas of sandbanks
contained little cockles in such numbers as several hundreds per
square foot, while the number of small mussels on a square
?
foot of suitable “ skear ”’ ground may run into the thousands.
Such invertebrate communities are the feeding grounds of
shrimps, crabs, starfishes, and young fish of various kinds
(plaice, flounders, dabs, soles, cod, whiting, sprats, etc.). Here
small plaice feed greedily upon Copepods, small worms, little
periwinkles, and very small bivalve molluscs, while the larger
fish eat the small Mactra, Scrobicularia, and cockles that are
nearly everywhere present in the sand. In the spring and early
summer months the temperature of the water on the nursery
erounds rises several degrees higher than it is offshore; the
tides run more strongly and so distribute the dissolved food
substances used by the Diatoms, Flagellates, and Dinoflagel-
lates. The sunlight penetrates to the bottom layers of water,
overlying the sand, better than it does offshore, and this is
favourable to the nutrition of the microscopic plants and
plant-animals. The latter are then eaten by the shellfish and
the smaller Crustacea and worms, which are, in their turn,
eaten by the small fishes, large fishes, and invertebrates. As
fast as the fundamental food substances in solution are taken
from the water by the organisms that exhibit the vegetable
mode of nutrition they are renewed by the drainage coming
down from cultivated land and from domestic sewage entering
the estuaries and then the open sea. The higher temperature
on the nursery grounds accelerates the rate of growth of all
animals living there. Further, the conditions, as regards
temperature and density of the water, are more variable than
they are offshore because of the more rapid tidal streams,
freshets entering the estuaries, and the greater agitation of the
water by wind action. This variability in external conditions
101
is itself a stimulus to growth and reproduction, and to the
maintenance of a condition of health.
The shallow-water grounds off the coast, between low-
water mark and about 5 to 10 fathoms of depth, are therefore
the place of origin of all the young fish in this neighbourhood.
For about three years the plaice of the Irish Sea live here
moving a little out to sea in the warm summer months and then
returning inshore again for the period of the winter and spring.
They roam about to a marked extent, making quite long, winter,
longshore migrations, possibly in search of food and possibly
just from the general “restlessness” that is a fundamental
feature of animal life. In certain months, about December to
March, there is an evident scarcity of the small plaice on the
nursery grounds, and it is highly probable that they “‘ dawk ”
in the sand at the bottoms of the deeper, inshore channels,
covering themselves up so that only the mouth is visible.
Respiration slows down, the fish cease to eat, and their functions
are as nearly at a standstill as possible. The weight of the
body, in proportion to the length, decreases. If we call w the
body-weight in grams, / the total length in centimetres, and
c a constant, then we get the following formula :
100 73
E=
w
Now when we find the value of ¢ for the various months
throughout the year we see that it varies from about 0-8 to 1-2.
When it is small, at the period of about lowest sea-temperature,
the plaice is thin and in poor condition, and when it is large,
at about the period of highest sea-temperature, in the autumn,
the fish become plump. The decrease in the magnitude of c
means that the fish does not feed and that the substance of
its body is being used up to keep the heart and respiratory
organs in action. Therefore there is a wasting of the body
during the coldest months of the year.
102
The Rate of Growth of a Plaice.
The age of a plaice is found merely by looking at the
otoliths (or earstones). The sex is found by holding the fish
up to a strong light and observing whether or not it has a roe :
the latter is deeply pigmented and shows through the trans-
lucent body and skin. The earstone has always a little opaque
spot in the centre surrounded by opaque and translucent
rings : thus—
Nucleus alone—the fish is one summer old.
Nucleus + translucent ring—one summer -+ one winter.
Nucleus + translucent + opaque rings—one summer,
one winter, one summer, and so on: a translucent
ring is added during each winter and an opaque
ring during each summer.
The plaice in the Irish Sea are always hatched out m
February, March, and April, but, for the most part, in March.
Therefore, a fish caught in July, and having a nucleus only, is
four months old, one caught in September, and with only a
nucleus in its earstone, is six months old. So also, a fish
canght in October, and having a nucleus, two opaque rings and
two translucent ones, is two years and seven months old.
Usually we called the plaice 0, I, II, III, etc., years old, meaning
over 0 and less than | year of age, over | and less than 2, over
2 and less than 3, and so on. For the first year we state the
age in months, the number of the latter bemg the number of
the months that have elapsed from the middle of March up to
the date of capture.
The growth, then, for the first year is as follows :—
Up to middle of June... ... 42-2 mms.
i. July... Sect EOD pias
s August ... ses O2°Dy lies
i September coh, DOOr es
October ... 2 OWA,
2)
1038
After October the growth ceases until the following April, when
it begins rather slowly, increases up to about the middle of
July, then falls off and finally ceases again about the middle
of October.
Now the growth is very variable. Even in the same season
some fish of the same age grow more rapidly than others.
Plaice reared in Port Erin tanks showed this to a remarkable
extent, some (of the same year’s spawning) being actually
twice as long as others: this is individual variability. There
is seasonal variability: thus, fish of, say, two years of age
may grow more rapidly in one year than do the fish of two years
of age in another year. Finally, there are local variations :
thus, the English workers obtained the well-known result that
plaice grow about twice as long, in the same period of time,
on the Dogger Bank than they do just off the Dutch coast.
The following table (No. 14) gives the results of the
measurements of 7,724 plaice, all caught on the nursery grounds
and on the inshore grounds, and mostly within the territorial
limits. The table, therefore, represents very well the kind of
plaice to which regulations, restrictions, and prohibitions, of any
kind, would apply.
A few words of explanation are necessary :
These are all plaice caught by shrimp-trawls (of 2-inch
mesh) and fish-trawls (of 6-inch mesh). Now a shrimp-trawl
will, in theory, catch plaice up to any length, but if it does take
a fish of over about 25 cms. long, say, there is always the
chance that the latter may swim out again through the mouth
of the net : this is because there is not a very great “ draught ”
of water through the very narrow and close meshes of a shrimp
trawl-net. Therefore the latter tends to wnder-sample the
larger fish that are on the ground over which it is dragged.
On the other hand the 6-inch meshed fish-trawl will not catch
many plaice less than 10 cms. in length, and this is because
most plaice less than that length, and many of those between
104
Table XIV. Length Frequencies for Age Groups, O to IV,
1908-1916.
IHU | IV
Mean Length. | O | I Il
ZIG Spee ee aa nee igeee 20
Ta) SR Se See eet 213 |
Ge Diesen cetera 368 | 13
TOS nes BOOC nan OOO SAT aC OOH 317 24. | :
QDs teseneeseona eens 151 26 sue
G5 sccibte aleiers s(sisisie ele eiarsteciare 65 56 | 1
NOs Diaccsdcbapeeteesecnee 32 95 2
Lilie ce cosveschecceeeecesce 20 151 | 2
Haas Seaton coonéodanacnncccae 16 189 9
Be aircarsiatcte slorsteletetewe'e s esicrees 6 258 | 45)
A Sach ce see aniston wie astnais 3 | 276 | 17
Stes aadacesweesecerenees wine 300 7)
UG sia sevee nclcniensie oe come cles 22 165 seis
Te bscassaccesenoccsenceres 256 | 278 1
USB pac sncostecsaeuek sesres | ile? 428 3)
NOs Dincrcnss cdeeocacnnwaets 118 | 479 19
Dey eauscnranoe Yoeeoeacae ete 65 490 2]
Wty T Aasins sass oeclsseeeeeess } 31 425 34
DD Asiatic ware Sanielslosstenictce a 18 364 24
DS Edimcicre sicislele'e slalslewiemresie sieves 13 280 22,
DA Din ease wapeuseu ssa: | ac 8 207 32
DF Dyes ect seeetat cede seeaee das 3 148 | 29 1
Tete Anpe ey ett 28 Ke es 2. | 92 | 35 I
Dl DicMeomateeaceaeemee sees 65 43 AG
2S 5a aa aU ERS SOU IaSaec 39 36 2
DOs tye EF se calcination tance De 38 6
URS a onaneennebeTnoenaeccendc 9 29 5
Bila aancamapacdceccchetEnen 1] 20 6
BOT eee ests ene chan cerence see 5 24. 1
SBD Msnctanses srenasecieescus 1 10 2
8 LATS sopndcsousagauncostena 2 8 8
32725) \awlooaie cersivleteinie siaisleisisveisios | 5) 7
SG25 cchitenieceueascteeeesce 5 22
BT caeamencioonons meter eals| 1 2
SBUBe whan ee eeonesceetere 3 2
BO Hats se sansstnenocsontsacos il
EGS Roanucncoeaecocrnoranc ne
(UNG) OUR PERS Sei mcs 2
Notalssicssce- see csesconnes 1,211 2,385 | 3,638 442 48
Mean Lengths ......... 11533 15:3 21-0 26:8 | 32-5
Standard Deviations... 1:58 3:18 2-63 4:34 3-70
Shortest Half-ranges.... 5-8—7:5 | 13-5—17°8 | 18-5—22-5 23-9—30-2 | 30-8—35-8
105
10 and 25 ems. in length, can escape out through the meshes.
Thus the fish-trawl tends to wnder-sample the smaller fish
inhabiting the ground over which it was dragged.
We cannot allow for this by using both a shrimp-traw!
and a fish-trawl at the same time, for we don’t know exactly
how much time to give to each method. We cannot employ
a compound net, that is, a small-meshed one laced round about
a wide-meshed one, for the small-meshed net restricts the flow
(or draught) of water through the large-meshed one and so
impedes the action of the latter. Table 15 shows that we get
a different result for the Age-group I, according as we use the
shrimp-trawl or the fish trawl. Therefore we have added
together the results of the fishing of these two instruments
and then made some rather arbitrary corrections, which,
however, are probably “ quite all right.” Thus we get the
Column “I” of Table 14.
Observe here that we are dealing with a characteristic
“small-plaice ” area. We might sample Luce Bay, the Solway
spawning grounds, Beaumaris and Red Wharf Bays, each at
its appropriate season, and get much bigger plaice. Sfal/, in
regard to the operation of any restrictions or prohibitions,
Table 14 shows us what are the kinds of plaice which will be
affected.
It will be seen that a plaice of length of 25-5 cms. may be
1, 2, 3, or 4 complete years of age—and this represents an
apparently wide range of variation. But the table also shows
that, in all, 181 plaice between 25 and 26 cms. in length were
measured (that is, 181 out of 7,724 fish that were examined) ;
that 3 of these belonged to Group I, 148 to Group II, 29 to
Group III, and 1 to Group IV. Therefore, the chance that any
plaice caught at random belongs to Group II are 148 in 181 ;
that it belongs to Group I, 3 in 181; that it belongs to Group
III, 29 in 181, and that it belongs to Group IV, 1 in 181.
These are the “‘ odds ” in favour of the ascription of the fish
106
Table XV. Age Groups: Data for Group I, 1908-1916.
Caught Caught | Formed by
in in | completing
Mean Length. 6” mesh. 2” mesh. | Total. last series.
Tit eae Pes Cae AS 13 13 13
Te ce te, ee 24 24 24
tne Wea AR AREA 26 26 | 265
LO ES eae eas een Sere ee are 1 55 56 56
NO: ae se a | 4 91 95 95
WIth tee diac) Seema 6 | 145 151 Pecpatar
5 Pe ee en ae ere ll mags 189 | 189
1 Deo cece eee ee 12 151 163 | 258
CE Oi sh ae aan 6 136 162 276
Lbea ices eer ee 91 | 89 180 300
Gs Deeesaetes seca ee aeeneare 186 68 254. Dil ,
Weoeeteeeeeee er cea 215 40 255 | 256
1 ee ee eee 193 | 20 213 | O13
105 hoe eee 110 | 8 118 118
yy ee ie? eG 65 ae 65 65
DIRS 2 ek eee ee 29 2 31 31
DO Ae ah Ae 17 1 18 18
AH AALS es he en 13 | Me 13 13
YS SE gant PERL 8 8 8
SEs ONY cioerancie ie ons alaiesieeicerneeeries 3 3 3
Matai gee em meee cake 990 | 1,047 2,037 2,385
| "| oe Sr
MGA Steiacaseerec cee cereal | 15:38 | 15-28
| 3-405 2-142
Standard Deviations......
to any particular group. Really the odds will be a little
different when we apply certain necessary corrections, but we
shall only do that when required by the administrators. This,
then, indicates the way in which this (and the other) tables
ought to be used practically.
Fig. 7 is a graph of the results of Table 14. It shows the
average lengths of plaice of Age-groups 0 to IV, and also the
‘“ dispersions,’ so that some idea of the significance of the
overlapping of the various group-lengths may be obtained.
The graph is not a straight line, but a logarithmic curve of a
kind, and to see how this is we must consider the sizes of
ea he
107
plaice of each monthly age during the first year of life. So far,
however, we have hardly enough data to enable us to do so
b>] u fo)
satisfactorily.
Age. érovp AL)
Age Grovp ME) 7
ES Aes AéeCrop CAND) 1
X = hositron of mean
Gea
The Ratio of Males to Females.
We don’t know what is the ratio of males to females in
the first year of life, but it is probably one of equality. This
is also the case (probably) for any year group up to about HI.
After that, however, a very curious thing happens ; the males
diminish in number relatively to the females. This is shown
by the following statement, based on the numbers of mature
females and males over 23 cms. in length captured on the
Solway spawning grounds and adjacent regions in the spring
on IG PA
Size in cms. fon) AE Ody OX, D7, IS Ot) BIOS Ble ie 33, 34, 35, 36, 37, 38
Females... soe O, Oy “As 0, i yD WO fy Gh Ia, NOs Wy, Ga 1a
Males eats olson 64. olor OOo 455 45, 43, 46, 44, 37, 30, 22
Size in cms. ... 939, 40, 41, 42, 43, 44, 45, 46, 47, 48, 49, 50, 51, 52, 53
Females... Soe HIG BAO, AKG, PAS) A), Bia, BRE ER I BE ce Rh a)
Males ane LOM Seo Some oe Ome OOS TO TO Os Ol O% #0
Size in cms. ee ae «. 94, 55, 56, 57, 58, 59, 60, 61, 62, 63, 64, 65
Females ... ate sy soo Oe BE Oe JOS Th WOR Oy O. Ohe ile Oe ol
Males ... eRe eae sco OS @ Wn Os Os Wh Os © OO O, ©
Thus, the females caught are always bigger and older fish
thanthemales. They grow alittle faster. Theinteresting thing
is that the males apparently die off at a greater rate than do the
females, and this probably represents a general law among the
108
marine animals. Hverywhere the female is the dominant sex :
usually bigger in body, longer-lived, and predominantly the
more actively metabolic animal of the two. This is so in such
fish as the plaice, sole, turbot, etc., where the mass of material
converted into sexual products by the female is always much
greater than in the male. The ovaries in most fishes are bigger
than the testes. The herring, however, may be an exception,
for here the two “ roes,” hard (or ovaries) and soft (or testes),
are of the same size.
The Sizes at which the Plaice become Sexually Mature.
Not so much has been done on this point as we would like,
but some observations will be found on p. 92. The smallest
mature female found was 26 cms. long and the largest immature
female was 42 cms. long. | 2013
40°5 2) 0:03 31 O16 | 1| 0-07 2| 0-08
415 l 0-02 1 0:05 | 5 rn oe
42:5 1 0:02 ely on 1| 0-07 1| 0-04
43°5 fs ee ye 1 0-04
44°5 - 1 0:05 1| 0-07 - a
45°5 1 0:05 1} 0-04
46°5 | ee ; a
475 | a,
48°5 ie
49°5 2 0:03 |
50°5 0:02 = hs |
515 er 1 005 | ... |
3,560 | 10004 1,823 | 99°92 1,338 99:96 2,421 | 100-01
143
The results of Table 16 are studied by making shortest
half-ranges from the various yearly distributions.
30
Fie. 17. Variation in length (shortest half-ranges) of plaice caught
on the Mersey nursery grounds, during September and October, 1908-1920,
by a trawl-net of 6-inch mesh.
The figure represents the prevalent sizes of plaice on the
above grounds. The lengths of the columns, read off on the
scale on the left-hand side, give these prevalent sizes. Now
the latter certainly increased regularly from 1908 to 1911
(which latter year was about the time of a maximum in plaice
abundance), but after 1915, when there should be a minimum,
the prevalent size of the fish does not increase towards another
maximum about 1920, as one might expect. Perhaps, to expect
so much would be foolish for we may have to reckon with
the fact that the migration periods that we noted above may
be variable—and here we have studied two months only.
In fact, this question of variation in length is very complex,
and we are still without the knowledge that would enable us to
deal with it satisfactorily.
Fluctuations in the Size of Plaice—Liver pool Bay.
Next, we take another region, Liverpool Bar to Blackpool
(mostly within territorial waters). All experimental fishing
144
was suspended here for the period of the war and we have
only the years 1909, 10, 11, 12, 13, and 1920 for comparison
with each other. The distributions considered are those for
August and September (the best ones), and the data are taken
from Tables 5, 23,24. What we can compare is the pre-war
period, 1909-13, with the post-war one, 1920, and it is to be
noted that we know nothing of the years 1914-19: possibly
1919 was a year in which the plaice here ran bigger than they
did in 1920. Now which of the pre-war years ought we to
set over against 1920 ?
The last pre-war year, 1913, is the one with which we
naturally compare the first post-war year, 1919 (or 1920, for
we have no data for 1919). But we see, from Fig. 16, that 1913
appears to have been a year of minimum abundance of plaice,
while 1910 was situated near a maximum. It is well, then,
to see if there are differences between the prevalent sizes of
plaice as they occurred on the Liverpool Bay grounds, and so
Fig. 18 was prepared.
Evidently, if we compare 1920 with 1913, we find that
the post-war plaice ran bigger than did the pre-war ones ;
but if we compare 1920 with 1910 we find that there is little
(if any) significant difference. I{ we take the average lengths
for the years 1913-1909 we shall find that the plaice of 1920
are, on the whole, bigger than in the years immediately pre-
ceding the war ; but it would be wrong to associate the increase
so indicated with the restrictions on fishing of the years 1914-18.
It is necessary to consider also the deviations from the average
of 1909-1913, and we see that the good year 1920 is not any
better than the best of the pre-war years with which it is
contrasted. The fact is that these length-frequency data are
very difficult to interpret in some cases: to make the best
use of the information that they give requires also a knowledge
of the migrations. We should want to know, rather closely,
in what months the crises of the migrations occurred, because
145
we are comparing a definite period (August-September) in all
the years, and it may be the case that large plaice had left
Liverpool Bay, in greater proportion, and in a certaim month,
in one year than in another.
ail | eee — = = Saree ys eee = ee
[ELMS DOD AORTA ENDS. IST I IS OT 27. |
trawl-net on the Liverpool Bay grounds in the months August-September
during the period 1909-13, 1920. Summational curves, from Tables 5, 23, 24.
The Northern Plaice Grounds in 1920 and 1921.
There is material for an interesting comparison in the
data obtained on the northern grounds in 1920-1921, when
investigations into the spawning of the fish were made, and
when we were able (by permission of the Fishery Board for
Scotland) to trawl in Luce Bay. The Table 17 gives the
leneth-frequencies tor the months of January to April, and for
the ‘‘ Shoals ” and “ Slaughter ”’ grounds (the latter being that.
on which spawning fish were found). Fig. 19 is a graph of these
data, and also the results of the hauls made in Luce Bay in
1920-21.
K
146
Table XVII. Northern Crounds, 1920-21. Length Frequencies.
** SHOALS.”” ‘* SLAUGHTER.” SoLway SPAWNING | LucE Bay.
GROUND.
| | |
I ie | TV. Pe ne.) TV. | 9) ae ave S208 eiaoee
15°5 a 2 aT as 6* eee Saleen 6
16°5 Dale Pi eee. eS i 2 2 3 pA) Ts
17°5 PST NBs Rita a ANAS 1090) 7 6 3 | 47
18°5 Be S28 al) ul meee 4|/ 5/ 4 Sr a3 5 9 Pa at oS:
19°5 2 aes © fas fe nents oe Meese Sel ol pst 6 | 46
20°5 12| 30| 6 Oe POel er Grl s P1e 2S |e a ete 4 Balaeal
21°5 10°), 30) 104)" Se 29. Si) 755) Os Se elo eee 6| 14
22°5 127) 034 en 2 Selle 2 1S) eS aeeG 8 5 | 15
23°5 AD ST 6 934 Sale 185) 6.) aI Sa ees : 17
24°5 D1 S29 Rea jane 2 7 S|) 2 2) lees 6 4 6
25:5 DO AG Gat Doin aT a rales 5 1h Sea etna a4 3 | 15
26°5 133), 135) as 5 | 155) 20 2) 131) S62 ls 5 6
27°5 SA Sa eal weet a) eS 1 OP Ser lmees 7 tae!
28°5 (a by, 7 aeties |pe ts 57) 3 | 8b" ean 22 S40
29°5 al Te) | Sallie ae ee 1 2" 49) 728 9 3513
30°5 3 5 Qi By agk | ae 4 || 3) 255) 18a) ie 6 | 10
315 3) 8 Br) lt jee Fi ike ShaleasOniy 24s | 110) 4) 93
32°5 Selheals api ily) Pies) ile ies. erooey) 10 8 5| 18
33°5 Pad a0) aah fea al ee se Sal 2s) 387) 14 8 7 las
34:5 2 9 Tse alee Greek Wl Oey pa S|) @25. eee
35°5 3 81 2 i wees Selena eos 1 623 S| 1O"les
36°5 6 6 An 2 9 3 | 30 | 12] 12) W923
37°5 Re ER eal biceps ele | 3) | 34) 15 | 10 on eat
38°5 2 Sule at eal 5 | 10 2 2) 20 9 6 | 2saeay
39°5 Weyer seael | a. 33 Bal US| Cee een cool: 0 9 | -10)) a
40°5 5 4 3 fi 6 2 13 7h 9)| 12
41°5 a eee 6 7 1 13 6 2) 125 arG
42°5 ey ak Bia ces 7 8 1 |) 26.) 10 BRL y -7/ 4
43°5 een, soe wl aT 8 5 1 14 5 3.) atl 4
44°5 1 35)" 1 9 8 1 algae: 6 5| 6 3
45°5 Fs gees ie 1 6 8 1 lly 2 7 4 3 1
46°5 5 1 1 1 7 2 1 3 3
475 3| 4 1 2 8 | Ged 2 mu 2
48°5 Sil hic eee es eee Ball eee | tkneee 3 1
49°5 Bi gee 1 3 1 5 1 1 3
50°5 1 1 1 ih 2 D . 2
515 aeons 1 1 1 1 2 ; 1
52°5 eee 3 1 | 5 1 as 1
53°5 1 1 1 3 2 1
54°5 : Pe 1
555 1 1 1 2
56°5 1 +
515 a | 2
58°5 1 | 1
59°5 Sats ons
60°5 | ae
61°5 | as
62°5 ;
63°5 1 Wy :
65°5 ; | A eae WAH soe Ts) pee eg Gee hd) eee 1
133 | 449 185 | 70 | 313 | 367 | 77 | 133 | 927 | 469 | 279 | 194 | 558
147
These results represent the biggest plaice caught anywhere
in the Irish Sea area. Here we are concerned only with the
Luce Bay figures. The graph shows a fairly well-marked
difference between 1920 and 1921 for this region, the plaice
taken in 1921 being considerably smaller, on the whole, than
those taken in 1920. Now a somewhat similar decrease in
size in North Sea plaice, in 1919 and 1920, was held, by the
= PS
oS x ~.
Vig
(e) Ah
Summed | x ry \Y
Northern Plaice Grounds
I9LO-21 |
Length. cms.
Fre. 19. Graphs of the length-frequencies of plaice caught in a 6-inch
mesh trawl-net on the northern grounds in February-April, 1921, and in
Luce Bay in September, 1920 and 1921. Summational curves from Table 17.
English workers, to point to the first results of the renewed
intense fishing of the North Sea. That explanation is difficult
to extend to the Irish Sea area, for there is comparatively little
fishing in these northern grounds, and Luce Bay is, of course,
148
a preserved region, where all forms of trawling are prohibited
by the Scottish Fishery Board.
Relative Proportions of the Age-groups of Plaice in the various
years.
Hitherto it has been rather suggested that plaice are
bigger or smaller im one year than in another because they grow
more or less rapidly. No doubt there are differences of such
a kind in various years, and, no doubt also, these differences
depend on a greater or less food supply. Just yet we have
very little information about variations in the food supply :
the subject is a very important one and it is being investigated,
for the North Sea, by the English Ministry of Agriculture
and Fisheries. What we have to point out here, however,
is that the differences in prevalent length between the plaice
of a certain ground from year to year (such differences as are
represented by the length-frequency distributions given in this
report) depend principally wpon the composition of the shoals
of fish as regards the age-groups. This is the argument, worked
out very ingeniously by Dr. Hjort, for the Norwegian cod
fisheries.
Consider, first, the lengths of the plaice belonging to
Age-group III (over three and under four years old) and taken
in Liverpool Bay in the years 1908-15. The sexes are not
separated, and the numbers of fish measured in each of the
months June to November (the Roman numerals at the heads
of the columns) are given separately. The mean lengths of the
plaice in each month are given at the bottom of the columns,
and we see that this increased from 23-0 cms. in June to 29-5
ems. in November. Thus we have a mean increase in size,
during the growing season of the year, of about 7 cms. (for we
must suppose that there was some growth in April and May,
for which months we have no data).
149
Table XVIII. Lengths of Plaice of Age-group Ill, ¢ 9° :
Liverpool Bay, 1908-1915.
Mean | | |
Length. | VI Arai VIII 1D x XI
| | fra
Go | 5p Sac ae
175 | 3 ns a 1 af |
18°5 4 | 4 1 pe nt
19°5 7 6 ne 1 na
20°5 16 | 2 4 1 1 1
21°5 16 5 10 1 1
22°5 10 i 7 7 4h | ies
23°5 18 10 7 11 an | 1
24°5 7 9 7 8 i as
25°5 a 9 8 6 1 | as
26°5 5 7 9 10 ae 4
27°5 4 6 6 4 3 oe
28°5 2 4 4 5 2 | 1
29°5 2 1 6 3 2 3
30°5 1 ts 3 2 | 3
31°5 1 4 4 1
32°5 nae l 1 2
33°5 a 1
34:5 1 1 aes
35°5 1 1
36°5 1
Totals ...... 104 74 Gir 67 11 19
Means ...... 23-0 23°9 25°4 25:9 | 27:3 29°5
Relative abundance of Groups II and [11—Liverpool Bay.
II Il Ratio of II to IJ
1908-16 500 pod 3,638 442 100: 12
1914-16 556 563 630 73 100 : 12
T9207 ea: ne sae 928 802 100 : 86
Next, we take the year 1920, for which we have better
data. Table 19 gives the results of measurements of plaice
caught in Liverpool Bay during the months June to December,
distinguishing the sexes and stating the measurements for each
month separately. Also Age-groups II (over two and under
three years old) and III (over three and under four) are distin-
guished. Now it is obvious that the data for the months
June to August in the case of Age-group II are incomplete,
150
and this is because the trawl-net employed (one of 6-inch mesh)
did not sample the fish of lengths 10 to 20 adequately, many
of the latter escaping through the meshes. If we had had
representative samples of plaice of Age-group II of this range
of lengths the mean lengths for June, July, and August would
have been reliable: as it is they are not reliable and have
not been stated. (This selective action of the nets used is a
troublesome source of error far too frequently neglected in
discussions such as this.)
Age-group III, male and female, are, however, more
adequately sampled and perhaps we can depend on the mean
lengths. Allowing, then, for a certain growth m May (not
given in the data) we may conclude, from inspection of these
tables, that the mean growth-rate for Age-group HI was about
7 cms. There is no reason for supposing that there is any
trustworthy evidence that plaice of Age-group III grew any
faster or slower in 1920 than they did in 1908-1915. If there
are distinct differences in the prevalent lengths of plaice
inhabiting Liverpool Bay in the period 1908-1915 and in the
year 1920 this cannot be said to be due to different rates of
growth.
Composition of the Plaice Stock as regards Age-groups.
Now we consider the relative abundance of plaice belonging
to Age-groups IL and III in all the fish measured, from the
Liverpool Bay region, in all the months, during various periods.
Sex is not distinguished. We have
Age-group II Age-group III Ratio of IT to IIT
1908-1916... 306 3,638 442 100 to 12
1914-1916... nee 630 73 100 to 12
US PAD) oac 36C eee 928 802 100 to 86
All these plaice were taken in the 6-inch mesh trawl-net and so
were the following ones, caught during 1909 and 1911; Age-
eroup I being also included in this series of measurements :—
Age-sroup I Age-group II Age-group III
52 46
1909 ces Ras 2 per 100 fish,
1911 sie ick 11 68 21 a
151
Table XIX. Lengths of Plaice of different Ages and Sexes :
Liverpool Bay, 1920.
AcsE-Group IT, MALE. | AGE-GrouPp II, FEMALE.
Mean |
Length. “Fe Pyrite we ae ees = iin el ae iy ree all
Vile avarie VAL ING |e XX HOD) WP) WEL. | VERE |, 1X D-Mnd.T Ne o.41
16°5 4 1 2 x ae a ads 4 re a 2 Fae l
175 ky us 33 2 3 3 eae 19 | 9 6 1 3 1 at
18°5 22 10 7 4 5 | 2 1 tO nets 8 6 4 2 1
19°5 VS7|7 <0 6 10 ll 5 2 12 LT 7 14 9 5 nis
20°5 9 4 14 24 16; 10 ] 5 5 4 16 8 3 2,
21°5 1 4 5 16 18 | 9 3) } 2: || 4 4 19 8 14 3
222i 1 | 6 22 14 | 18 6 Sill meee 6 12 7 11 4
Qe | 1 20 Wie eo 4 | Te) 1 1 10 16 zi Z
24°5 1| 14 EO aS 7 | awe : 5 5 19 2
25:5 one if ei a ae 3 | : 2 10 ui 2
26-5 ee aoe are a a & 4 | =| 2 1 5 Bae
27-5 | | 6 fit 3) | 5 1 a ;
28°5 Salar ett pack en, eH) 2
29-5 Pe eea ages
Totals... 69 | 32 | 45 | 124 | 105 | 100 30) eo 2 een 36 92 74 97 19
IMe@amsices\) ce ||| eae Son || PZB) || PPLE || 2283877 1 CBG} 28) 2220) 23:8) 22-9
Acs-Group III, Mate Aas-Group III, FrmMae.
Mean
Length | ; a ]
WAL |) WO WANT) IDs |) ox DML |) STL WAL fh WADE |) WAU B26) Oe || a2ar I) sant
16:5 OM Nace : a Al ee
ils) 1 3 : \ Panes 2 es é - ae ae ;
18°5 8 5 ae peers u 4 oy 52 1 ees ;
19°5 16 4 4 aie tie 1 a 6 1 1 1 1 Ae
20°5 18 ZU 5 ae 5 1 14 6 1 sist 1 ] 1
21-1 10 55 2 8 PAA Msg 2 8 4 3 2, 1 és te
22:5 i a 2 enon nee 2 — 13 4 tad 9 4 son SRE
2320 2 18 4 4! 8 8 33 53 ll 3 8 5 3 1
24°5 7 14 11} 10} 4 | 5 3 19 4 al 3 4 4
20°) 1 8 3 11 | 3 Tn 8 ae 10 Ti 7 3 5 2
26°5 aoe 9 Age 19 | 7 8 | 1 ey 1 6 4 3 2
Disb ses 10 2 VE (a) j) JL 3 9 2 9 | 8 4 ee
28°5 8 1 2 8 6 2 4 2 3 5 4 5
29°5 5| 1 Teens) | * i ae le Borie 2
30°5 3 sea. 5 2 3 te 5 8 Uf
3311955 aisle } 4] 1 | 4 2 bas 4 1 5 2
32°5 os 4 | DAI Saelh ede : 3 ise 2, 1
33:5 3 aale Bibi ee aera michael Sore I hepetil saine Ah eee
34°5 Mts | ey |e | Aa see ae ae 1 1 aide
Totals... 72 | 106 29,0 ai | 67 | 62).|, 28 59 | 89] 28 64 | 44] 50 27
Means ...| 20°8 | 24°8 | 24:0 | 26:1 | 26-1 | 27°3 | 26°8 || 21-1 | 22°8 | 25-4 | 261 | 26:1 | 28-1 | 28-0
! | |
152
Now Fig. 18 apparently shows that the plaice caught in 1911
were markedly bigger, on the whole, than the plaice caught in
1909, and one might incautiously infer that the rate of growth
was greater in 1911 than in 1909. But the comparisons of the
composition of the shoals, both in the periods 1908-16, 1914-16,
1920 (Groups II and III), and in the periods 1909, 1911
(Groups I, II, and III) show clearly that the prevalence of
bigger fish in some years is due to the fact that older (and therefore
bigger) fish are more abundant in those years.
Causes of Fluctuations in Abundance and Size.
Why, then, are plaice bigger, on the whole, and on a certain
ground, in one year than they are in another? It is because
there are more older fish in the shoals in those years when the
plaice run bigger, not because there is a greater rate of growth.
No doubt the rate of growth varies to some extent, but not much
—not enough, we think, to account for the differences that are
to be observed from year to year.
Why are plaice more abundant on a certain ground in one
year than they are in another? It is because more fish have
passed successfully through the critical periods of metamor-
phosis and have managed to settle down on the nursery
grounds, there to grow rapidly and safely. If there are more
plaice of three years old on the Liverpool Bay grounds in the
summer of 1920 than there were in 1919 (say) it is because
more little fish came on to the nurseries in the summer of
1916. And so with each age-group.
The abundance of plaice of any particular age-group, on
a fishing ground, depends, then, on a number of conditions,
all of which have, by some happy chances, been in existence
and have been correlated.
(1) There must have been, so many years previously, an
unusually large production of spawn.
(2) An unusally large proportion of the larvae hatching
out from this spawn must have metamorphosed
successfully.
153
(3) The larvae must have found suitable food in the plank-
ton on the sea area where they metamorphosed.
(4) Suitable wind-drifts, tides, etc., must have brought
them to a nursery ground and not to some unsuit-
able part of the coast.
(5) There must have been plenty of food on the nursery,
with other suitable conditions.
To test all these conditions is quite possible—and_ it
would be the most fascinating kind of research imaginable.
Just vet the resources for such investigation do not, of course,
exist and so we cannot offer any data. But even the inadequate
material we do have at our disposal may carry us some way
and so we have prepared the following Table 20. There are
marked differences between the prevalent sizes of plaice taken
in the shrimp trawl-net in different years, and these we are
considering. We have included all the measurements of plaice
caught in hauls with such nets (of 2-inch mesh) in the months
October to March of 1908-9, 1909-10, 1910-11, and so on.
By October the fish have ceased to grow, and it is April of the
following year before growth begins again. Therefore we can,
from a study of the relative abundance of very small plaice
taken during the winter months, endeavour to obtain a measure
of the numbers of plaice spawned, successfully metamorphosed,
and transported to the nursery grounds. Thus we have
prepared Table 20 in order to make such a measure of the
productivity of the various years for which we have data.
Looking at the length-frequencies recorded in Table 20
we see two kinds of distribution: that of the years 1908-9,
on the one hand, and that of 1914-15, on the other. Small
plaice of less than 8 cms. largely preponderate in winters of
which 1908-9 is the type, while in the other kind of winter,
such as those of 1915-20, the small plaice are much less frequent
in the catches. It is hardly necessary to examine the small
fish taken in the shrimp trawl-net in order to find what is
their approximate age, for we can be pretty certain that
1éG 99F'T 8L0°E 1&9 SIé‘T GFL‘G 828% | SSL‘E SLE°SE| sPre’e 960°F 6686
wee tae eee eneeeeee
wee see Stee eee eeene
eee we wenee
teen ee ewes
te eee eeee
Stee w en eeee
| PE
G If GP LT SOT €LI 9G | 68
8I FL gg 89 gel terete) GE | 966 | at
€¢ LO | §&I SII O&T StP OF | 9&€ 6G | GOL 86 06 ae ae
&@ OST 891 6e1 18 G88 IP gig | Vel G0G T6 GL eile a
1G L8T EPG G8 €8 1¢0'T 8L 0g FIG OGG 60T 611 pales ads
GG LOG CFG IL TOL 9GL 99 609 | ILzé Ilé Sol Shi ok ae
09 [0G HIG 8é v8 O8P 9L (pale CbG CEG VEG FOG pa a
GL. 691 | GGE 9 L& | 9&P 901 O00OG | FEST GLY LOF 90a baie
; | 666 PIG Sol | 0067 FIG 809 COCs alictaeons
i
ioe)
=
4
ioe)
| td
No)
—
q
UD UD UD UD UD UD UD UD 1D UD 19 1 UD
wD
1 14 1
1d 1) UD
ONO HINO DODO ANA O H 19 OE OS
Oe Se Oa ee Sa fot ala ok Ga ON CN IGWIAN GlICN CN CWE
lo
sD
08 GL CPG 61 OP 06G €G¢ | SLT | €éPr6 FES 819 COUT ales t cs
Cie) 88 n08 |= 8e8'- | 6. | 9LO'OT\/c9c6, | ono)” | -eeeia tes
7G ¢ Me fon 68 ora | s89 | sob | ool | ori | ceo | corn
G SI OZ | 8 een | SIP ILZ R89 eCZ |eceeeeeee AO
1 1G UD 1
Jose oe Seas
‘0G GIGI | “6-SIGT | “S-LIGI | “L-9161 | ‘9-SI6I | “S-FI6T PSIGL | “E-CIGT @LIGL ; “L-O16L |OL-606T | 6-806T
"Bary Aassail > 0361-806! ‘Y2ARIN-"}90 SULNP JON-|MUAL duAYS UI pYSNeD edIeid “XX GUL
155
about 90 per cent. of al! those that are less than 8 cms. in
length belong to Age-group O. This arbitrary limit has
therefore been taken in Table 20, and the proportions of
plaice of less than 8 cms. long have been calculated and regarded
as giving us a good idea of the relative abundance of young
fish resulting from the spawning of the months March and April
immediately before. In this way Fig. 20 has been made.
40
1908 1909 1910 19/1 19/2. 19/3 10/4 1QIS 19/6 19/7 19/8 1919 192.0 1921
Fie. 20. Graph showing the productivity of the spawning seasons
during the years 1908-19. The heights of the rectangles are proportional
to the numbers of plaice larvae reaching the nursery grounds.
We see that 1908-11 and 1913 were good years in that
large numbers of young plaice came on to the nursery grounds.
The years 1912, 1916, and 1918 were bad ones—years in which
there was an unusually small production of young plaice.
It would be unprofitable to pursue this matter further,
for hardly any data exist, just yet, which would enable us to
look for the reasons why some years are better than others.
Tables 21 to 27 now follow: these give the results of
measurements of plaice made in the Irish Sea during the
year 1920, and they are intended to provide the data for more
minute comparisons with the pre-war period than we have
now the opportunity to undertake.
156
Table XXI. June, 1920, Irish Sea: Plaice taken in Fish Trawl.
HU OUT UU OUT SUAS AU UU
SWWWWWWWWWNNNWNWNW hb bo
PADUA OWA SSHISUR EIS
INSHORE GROUNDS. OFFSHORE
GROUNDS.
Length. LIVERPOOL MERSEY NortTH | CARNARVON Via, Vis.
Bay. ESTUARY. WALES. Bay.
f ges fiw lee if Piles f Folge if Seales
ane 19 | 15:5 Bs coe sea | ce 1 2°4
ae oe 70 Byeil |) il 4 1 9°8 me Ae
11 L225 164 134:0 1 4 2 19°6 Ih 2°4
24 PAL BY | AKet#) 154°2 3 1 5 | 49:0 33 eZ,
119 135°4 | 186 151-7 9 36 1 9°8 3 die,
170 193°4 | 196 159°9 21 84 1 9°8 12 28'8
166 USS:Siaa lesa 04:4.) 18 Te 4 39°2 6 14°4
14551) 65:0 84] 68°5 31 | 124 5 49-0 6 14°4
81 92°1 | Oomltose 30 120 7 68°6 10 24:0
48 | 546 46| 375 | 19 | 76 7 686 | 16 381
45 51-2 | 23 18°8 17 68 12 EG 15 35°9
30 34:1 25 20°4 17 68 10 98-0 15 35°9
16 18:2 15 2s, ily 68 8 78°4 22 52°8
9 10:2) 1) 107) 81 10 £0 al? 117°6 28 67°1
1 | 33 | 2°4 10 40 12 117°6 40 95°9
3 3°4 6 49 | 10 40 7 68°6 32 76°7
2 2B} 2 16 7 28 1 9°8 37 88°7
a. Le 6 24 3 29°4 35 83°9
2, 2°3 4 Geel: 9°8 23 55:2
: Ade } 3 | 12 Bae ae 30 71:9
. er | 4 | 16 2a 50°4
: Ba howe | 8 ape 14 33°6
2 23 (Paes Rr | 4 1 9°8 15 35°9
1 | iMeali | i | 4 1 9°8 11 26°4
dé eae 4 vas 5 12:0
i } 1 4 ee 8 19°2
| 2 23 fa » 4 9°6
owe ne. 8 | sae A wd 4 ah 1 2-4
l IPI 1 Or8r ii sce aa Pe 2 48
1 Veil i 08 ul 4 il 98 1 2H.
3 12
| 879 | 999°8 1,225 | 999°3 | 250 |1,000 | 102 999°6 | 417 | 999-6
Table XXII. July, 1920, Irish Sea: Plaice taken in Fish Trawl.
157
Mean
Length.
ID CUR Co hor
SNM RR Re Re Re Re Re Re
ICs Tt He CO RIES S
UC OU OU OUST SUSU SUC SUSU SUS OUT OU
bo bo kD by by bo
SSHAANEWNHE
INSHORE GROUNDS.
OFFSHORE
GROUNDS.
LIVERPOOL MERSEY | NortH | CARNARVON Ville
Bay. ESTUARY. WALES. | Bay.
ii th des f aaiiae i ES if ial os J ine as
ge | Spats Th eo. | - ds sn
ee ee 35 | 28°6 | 4 Se a A ae
cm eee 102 83-4 2 1:6 anes “ a
if al 1:8 144 | 11777 | 17) 1874 = 1 0-8
8 14:7 187 | 152°9 51 40°3 1 54 6 4-5
52 958 140 | 114°5 86 | 67:9 ce ae 25 18°8
67 123°4 83 67°9 123 97:2 l 54 49 | 368
39 71°8 65 531 117 92:4 2 10°8 100 | 75:0
33 60°8 54 44-1 | 112 88°5 3 16:2 135 101-2
20 36°8 BL | ALT. | 395 75:0 9 48-6 145 | 108-8
25 46:0 44 36:0 118 93:2 iva bod 160 120-0
37 68:1 61) 49:9 | 125 98°7 19 102°7 108 ~— 81-0
44 81:0 39 31:9 110-869 16 86°5 126 94:5
39 71-8 42 | 343 | 83! 65:6 | 23 , 1243 78| 585
51 | 92-9 20 | 163 59 | 46-6 25 135°1 84 63:0
$8. | 70:0 25| 204 | 41 32:4 16 86°5 67 50°3
32 58:9 29 2377) 40, | 3204 33 178°4 53 | 39:8
16 29:5 19 15°5 25) 19°7 11 59-4 47 | 35:3
14 258 8| 65 10/ 79 8 43-2 32 | 24-0
5 9-2 TQ eo Selre' 9 | er 7k 3 16:2 39 | 29°3
8 14:7 GON fez | 7| 55 2 10°8 29 21:8
7 12°9 5 4-1 12} 95 2 10°8 17 | 12:8
2, 3°7 8 65 8 6°3 ie 19| 143
2 3:7 OF Tt Gap 27 E 6 45
1 18 4A (33 4| 32 1 0-8
1 18 3 pr ee | Bee 1 0°8
ne ae 1 0-8 | 2 | 1°5
ee . ah 57 ae 1} 0o8
an aS 5 4] Ee Tol) Os
l 1:8 2 | 16 en 2 2
14 ae 1; oO8 1 0:8 -
ie 2 1:6 | : ae
. ee eee | eee
1 0°8 ae
1 08 oe
£ as 4 1 0:8
| eels
| |
543 999°7 1,223 | 998°5 | 1,266 1000-0
|
185 999°7 | 1,333 , 1000°5
158
Table XXIII. August, 1920, Irish Sea: Plaice taken in Fish Trawl.
Mean
Length.
O00 VSS QUES CSRS F210! S31) G3 Gu HX 09 RS
CULOLOU SUSU OL OU SUSU CUCU CE OU CUCU OL OLA A OT OA OT I
WWWWWHWHWWWNNWNNNNNNNNR Re ee
SASHA WYSSSHO1
INSHORE GROUNDS.
OFFSHORE GROUNDS.
LIVERPOOL |
Bay. |
Se odaee
1 0'8
9 ices
Sono led
102 | 83:0
123 | 100-0
162 | 131°8
TSS W222
108 | 87:9
110 89°5
87 70°8
73 | 59°4
55 | 44°8
49 | 39°9
57 | 46°4
38 | 30°9
31 25°2
20 16°3
9 83
7 5:7
4 Si}
3 | 2-4 |
1 0°8 |
il 0:8
2 16)
1,229 | 999°8
|
MERSEY Nort CARNARVON VIII... Vile
~ Estuary. WALES. | Bay.
f | F loo if Hiehioe if i Fan bs ij ries | f Jouine
| |
Tn 54 me = » e
37,| 28°8 1 132 ae ee es
147 | 114°3 se 2] 100 tos
163 | 126-7 : 2) 100 ce! ;
133 | 103-4 7 85 4 200 2 2°8 | x
122 | 94-9 45 | 54:9 2" | S100 157) 20°F <:
117; 91:0] 96 | 115-9 3| 160°) ) 2aeieare7 Shite
71 | 55:2} 99 | 120-7 1/ 50] 53} 741] 26
82} 63°99) 79 | 963| 2) 100) 64) 89:5) 51
59 ©45°9| 69] 84:1 2/ 100! 62] 86:7| 80
40 | 31-1 77 | 94:0 1 50 63 | 881 94
540) "42-0)| 58) |) 70-7 | 1! 50 56 | 783] 92
Sia e28'Sii, eo oe | eG4cGil ee 69 | 96:5] 105
34| 264] 45] 54:9] BI) 713) 07
34 | 264] 30] 36°5 | 61 | 85:3] 87
42 | 32:°6| 37) 45:1 42 | 58:7] 94
26 | 20°2| 36] 43:9 34 | 47:6| 65
16 || 12:4) 20 | 24-4 26 | 364] 52
25 | 194] 20] 24-4 125) 16 Sees
LOM © TS 15) 1456) 154) 20:5 14
127) 9:3 13 | 15:8 |) 5 15
6) 46 4] 49] | 9°8 10
i 0-8 7 8:5 Sal) ps2 1
31) 2:3 7 8:5 16 | 22:4 4
14) 40:8 3| 3:6 6 8:4 1
eel 1 1-2 2 2°8 | 1
See GIN oe 1 1:2 3 4-2 | 1
1) OS): eee ss 3 CED A eke
1 0:8 1 1:2 1 iA
Wiens a 4 56 1
s | 1 1-4 1 |
re | | 1 fe er
1 0:8 | |
| |
1,286 | 999°9| 820 | 999-6} 20 | 1,000 715 | 999:°0| 919
159
Table XXIV. September, 1920, Irish Sea: Plaice taken in Fish Trawl.
INSHORE GROUNDS.
Mean
Length. LIVERPOOL MERSEY Nortu |
Bay. Estuary. WALES. XCAe IXs.
ij | if We J f Wee 1G ' i Wen | I Hj Ghee J | ih Thee
10°5 | Tie roe
115 | 1 18 Fl aes
12°5 ’ 10 18-0 1 0-6
13°5 : te ae 25 45:1 4 | 2:5
14:5 2 0-9 5 6:7 | 29 52° 10 6-1
15°5 10 4:7 10 13:3 SR 56:0 18 11:0
16°5 6 2°8 26 | 34:7 29 52:3 4 | 2°5
17°5 Be gaye 46 61:4 i nee 46 82:8 45 |» 27°6
18°5 74 | 34:7 43 57°4 6 27:0 49 | 884 lll | 67:5
19°5 139 65:2 58 77°4 11 49:5 | 59] 106°5 178 | 109-2
20°5 203 95°3 70 93°5 24 | 10871 87 | 157-0 200 | 122-7
21°5 246 | 115°4 64 85°5 23 | 103°6 58 | 104°6 179 | 109°8
22-5 274 | 128°6 77 | 102°8 21 94-6 26 | 46-9 151 | 92:6
23°5 239) |) 12-2 56 74:8 17 76°6 28 50°5 100 | 61-3
24°5 191 89°6 56 74:8 17 76:6 9 16:2 78 | 47:9
25°5 154 72°3 48 64-1 15 67-6 LS ie 82-5 63 38:7
26°5 114 53°5 31 41-4 2D 99°] || BOR Z/ 51 | 31:3
27°5 90 42-2 33 44°] 17 76°6 12 21°7 54 33°1
28°5 96 45:0 34 45°4 12 54:0 7 12:6 40 | 24:5
29°5 75 35°2 26 34:7 15 67°6 5 | 9-0 46 28-2
30°5 51 23°9 14 18:7 11 49°5 3 54 42| 25:8
31°5 37 17°4 7 9°3 4 18:0 3 | 5-4 49 301
32°5 28 13°1 ll 14:7 2 9-0 | 33 20:2
33°5 37. | 174 9) 120 2 9:0 ie 46 | 28-2
34:5 14 6:6 10 13°3 2 9-0 2 3°6 337 |e220;2
35°5 5 2°3 3 4-0 - 30 18:4
36°5 5 Oe 1 1:3 l 45 14 86
37°5 1 0°5 4 5:3 18 | 11-0
38°5 1 0:5 I 1ic33 | 8:0
39°5 : 2 2°6 | 5 all
40°5 ie 1 1:3 2 1:2
41°5 Daleme Ors a . 3 1-8
42°5 Me 1 1:3 aoa ;
43°5 l 1:3 (eres
44:5 | oe 10 PO:6
45°5 1 1:3 3 | 1:8
46°5 see we
475 1 0°5
48°5
49°5 | eM ec
50°5 1 0°6
51°5 | ae
2,131 | 1000-0 749 | 999-7 222 | 999-9 554 | 999°3 1,630 999-1
Mean
Length.
CO OI ON I ON OO I ll cell cel
CRU SU SUSU SUSU SUSU SUSU THT UU SUSU
HKESOHDADARWNESHSHAANKEBWNHSOHAIBDUEWNIHOS
PRP WWWWWWWW WWI h
Table XXIV—Continued.
OFFSHORE GROUNDS.
1
60
IXc.
| if haeias |
| ha est hekees ox
| 1] 526
3 157°9
iI 52°6
2 105°3
2 105°3
3 157°9
1 52°6
| "3 | 157-9
| 2] 105°3
|} 1| 526
19 1000°0
IXp. 1X34. TXs,. TX43.
Go flee) | Flee. | 0 Nace eerie) mea
| wae | eee . on
| 8 10:0 2 375 30 200 ot :
| 29 36°3 1 Loy 2 | | goat 1 1-9
57 71°3 6 10-4 7 20-4 8 15:5
59 73°8 18 31:3 21 60°3 21 40°8
69 86°3 31 53°9 37 | 106:3 45 87:4
| 74 92°5 51 88:7 22) (63:2 63 | 122°3
| 59 72°8 41 71:3 20 57:5 81 | 157°3
74 92°5 52 90-4 22 63-2 74 | 143-7
56 70:0 47 81:7 29 | 83:3 ol 99:0
55 68°7 61 | 106-1 29 | 83:3 60 | 116°5
63 78:9 58 | 100-9 32 | 92-0 46 89°3
47 58°8 62 | 107°8 30 86:2 25 48°5
43 53°7 45 78:2 16 46:0 16 31-1
| 36 45:0 43 74:8 21; 60°3 14 27:2
| 27 33°7 23 40-0 Use) S17 3 58
| 25 313 20 34'8 15 | 43:1 2 3°8
| 9 11°3 6 10-4 yi) api 3 58
| 8 10°0 1 7-0 9 25:9 l 9
|) al 13 2} 3-5 3| 86 _
hoe 13 1) 47 ei 86 Wess
ren ‘ Dill) 16:7 i
| 33/17 .8-6r 1} Oe al ee
| . a 1] 19
on . see o- aoe
38 sibs
| l | ioy/
| |
| | |
800 | 1000°5 575 | 999°8 348 | 999-7 515 | 999-7
161
Table XXV. October, 1920, Irish Sea: Plaice measured.
Mean
Length.
=)
ee SS
GO 1S? OTH OS tS
9 NO) 5S COUT S9) OU HO BO) Onc 100) AS OU CR SS)
CU OU St SU GU US SUSU TC STU STUOUOTU SU TUT HTT TUT TU
ee Oo OO OO OO OOO
OAS oS w eOowe
oe
Iie)
Liverpoon Bay. | Mersty Estuary.
Ue are F Loo
5 | 13
a5) 7
3 86
5 256
ifs 281
33 +O 165
6 9:9 142
19 314 132
29 479 95
51 843 96
65 107°4 89
67 110°8 45
sl 133°9 51
64. 105-7 45
47 TTT 22
$75) 57:9 Dal
yy 52°9 25
22, 36°4 23
19 31°4 22)
32 52°9 16
9 14:9 10
11 18°2 10
4 6°6 6
3 5:0 3
2 33° 3
3 50
1 ie7/ 1
1
605 1000°2 1,672
NortrH WALES.
holes i Peles
|
eA Wiel oak ;
4:2 | 1 ii}
51:2 eis was
153-1 iT 13
1679 | 8 10°5
987 | 19 24:8
84:9 | 62 81-0
| 189 | 125 163°4
56:8 74 96°7
57:4 80 104-6
| 53°2 41 53.6
26°9 49 64-0
30°5 38 49°7
26°9 47 61:4
jess 53 69°3
161 41 53°6
15-0 36 47‘0
13'8 33 43°1
13:1 15 19°6
9-6 8 10°5
| 6-0 11 14-4
6:0 ai 91
3°6 4 5:2
18 8 10°5
18 3 39
Ss 1 “3
06
0'6
999°8
999:4} | 765
|
162
Table XXVI. November, 1920, Irish Sea: Plaice measured.
INSHORE GROUNDS. | OFFSHORE
GROUNDS.
Mean | ie.
Length. | LivERPOOL | MeERSEY Nort SoLway
| Bay. | Estuary. | WALES. Firtn. Xo.
Hh, ales | ij Tlb6 if fe oo | i i Slee f | f oles
| |
11:5 a sa hel ae
12°5 1 0-5 | 4 | oe
136 ies wir, MS 12:3 | | 16) ay
145 | 1 Ls 49 263 21| 62
155) | a 1 18 161 864 24 71
16°5 2 0-9 ar cf i 18 | 282 |) [bia Ws Sito
17°5 18 7:9 1 15-4 12 S11 | “272 P1460 ee 86
18°5 60 26°4 1 15°4 22 40-1 184 98-7 55 | 163
19°5 li 48°8 4 615 44 80°3 202 | 108-4 82 24°3
20°5 167 73°4 a mi 48 876 | 144 173 93 27°5
215° )'229)) 97:6 6 92°3 49 89:4 | 145 778 149 44°]
22-5 255 | 112:1 4 | 61:5 55 | 1004 | 106 56:9 | 212 62:7
23°5 294 | 129-2 3 4671 26 47°4 100 53:7 | 288 | S38
24°5 | 290 | 1274 | 3 | 461 S5 ep Ooser|) | bal 38°] |) so27 96°8
25°5 236 -103°7 11 | 169-2 36 65:7 43 231 | 352 | 104-2
26°5 143 62-9 2 30:7 31] 566 | 16 86 | 322 95°3
27°5 100 44-0 3 46°1 31 566 | 14 75 280 82°9
28°5 93 40°9 3 46:1 2 530 | 18 97 | 225 | 66:6
29°5 82 36:0 7 | 107-7 24] 43:8 7 38 | 210 62:1
30°5 59 259 4) 61:5 19 34:7 4 21 181 53°6
315 40 176 3 46:1 10 18-0 6 3:2 126 37°3
32°5 36) 15:8 | ss 15 | 27:4 1 05 | 92) (272
33°5 30 iS Srie | 2 30:7 16 29-2 4 21 77 22-8
34:5 7 Spe) l 15-4 4 73 2 11 57 16-9
35°5 19 8:3 1 15°4 7 12°83 | 2 el 50 148
36°5 2 0-9 ; 7 12S 3 16 | 35 10°3
37°5 2 0-9 1 15-4 5 971 f F 16 47
38°5 1 0-4 2 30:7 5 9-1 25 Pall 12 36
39°5 be oat 3 55 1) O35 6 1:8
40°5 ie 1 15-4 | 4 7:3 a 5 15
41-5 0-4 | 1 154 | 1 18 2| 06
42°5 1 0: ee 4 7:3 1 0:3
43°5 4 ik 1 18 I 03
44:5 : | : l 0:3
45°5 2 3-7 | 1 0:3
46°5 oe | . eee
475 a aK 1 15:4 |... ta) ate sax) pee
48°5 os, bbs a ti Ah cee3 ote. 1/12 gees ile) aise eed 03
49°5 a ae F: 2S he re oe ee te oe $
2,275 | 999-8 65 | 999°5 | 548 999:1 | 1,863 | 999°8 | 3,379 | 1000-2
|
Table XXVII.
163
December, 1920, Irish Sea: Plaice measured.
Mean
Length.
~
is . . . . . . . . . . .
TST Ot Or Cr Ot Ot Ot Ot ST St Oc St St Gr Gr Gt Ot Ot Ot Gr Or
SS
“
ee
: AL
Or Dr Ot Ot St St St Oi Or
| LIVERPOOL
Bay.
Re WOR OO
Cre soe Ole ST
to
SMOMMWA-TI-I1¢
~
999°7
MERSEY
NortTu SOLWAY
WALES. FIrtHu.
i alee i | bieal er
2, | 1-9
Si) aRe7
42 | 40-2
76 72:8
2 1-6 128 | 122°6
BY 152 | 1456
_ : 182 | 1743
10 8-0 129 | 123°5
27 216 87 83°3
29 23:1 73 69°9
42 | 33°5 59 56°5
40 | 31:9 40 38°3
44 | 35-1 30 | 28:7
62 | 49°5 Hd eatiss:
58 | 463 15 | 14:4
70) 560 4 3°8
75 | 59:9 4 3°8
HUST 30072 Dee
108 86-2 1 1:0
113 90-2 e
105 | 839
82 65°5 are
59 47°] 1 1-0
54 | 43-1 |
35 | 27°9
32 | 25-6
18 | 14:4
12| 96
8 6:4 |
9 2 |
7) 956
3) 2-4
6 4°8
7| 56
4 a2
1 0-8
2 | 16 |
3 2:4 |
6| 48 lee
3 2°4 :
1 0°8 | e
2 16 =
252 | 999°8 | 1,044 | 999°8
—
.
164
The Effect of the War Restrictions on the Fisheries.
It will be seen, then, that the results of the Irish Sea
investigations give little evidence that the restrictions that
were in operation during the years 1915-18 had any very marked
effect. Now we must not assert this conclusion as holding
for any other fishing region than that studied here: There is
evidence that the war restrictions had an effect in the North
Sea—although this evidence is not entirely convincing. So
far as it goes, however, it suggests that during those years in
which the ordinary intensity of fishing (that characteristic of
the pre-war years) was in operation, there was a gradual
falling off of the quantities of plaice landed, as well as in the
average quantities caught per day’s fishing. This decline
persisted throughout the years 1908 to about 1914. Then
followed about five years during which the existence of mine-
fields, and other conditions, greatly reduced the area over which
steam trawlers and smacks could fish. When it became possible
to resume trawling on a scale comparable with that of the pre-
war years it was seen that the quantities of plaice landed per
day’s fishing had increased. At the same time measurements
made at sea aboard the fishing vessels showed that the plaice
were, on the average, markedly bigger than they were in, say,
the year 1915. The natural conclusion was that the reduced
fishing in 1914-1918 had allowed the plaice, that would
otherwise have been caught, the opportunity to live and grow.
In 1919, therefore, there was an “* accumulated stock ” on the
North Sea grounds, the results of a period of ** protection.”
Now when the same argument is applied to the Irish Sea
grounds the same conclusion follows. There was evidence of
a decrease in the abundance of plaice during the pre-war
years and there was a marked restriction in the intensity of
fishing during the war years. In 1920 the size of plaice had
165
increased, and, on the whole, better catches seem to have
been made. But the evidence brought forward in this report
also shows, we hold, that this variability in the size and
abundance of the plaice inhabiting the Irish Sea is something
that happens, “ of itself,’ that is, quite apart from the influence
of the fishing fleets. Throughout the period 1892-1920 there
is good evidence of a natural fluctuation m the abundance of
plaice, some series of years being very good, while others
are relatively very bad. The evidence we refer to is all
experimental, but it is backed up by what we do know about
the fluctuations in the quantities of plaice landed by the
steam vessels and other trawlers working in the Irish Sea
area. Further, the conditions in the English Channel seem
to resemble those obtaining in the Ivish Sea.
If there had been no war, and no restrictions on fishing
in the Irish Sea, the result to have been expected would have
been just that which we actually observe—the progress of a
natural fluctuation in the abundance of plaice. If only the
measurements and other data which we give here, or which
are otherwise obtainable, were at our disposal, and no knowledge
that there had been a state of war during the years 1914-1918,
we should have been quite unable to deduce the latter. All
we should have known would have been that, for some reason
or other, vessels did not go to. sea so frequently in 1914-8 as
they did in the year previous to 1914.
These results obtained from a study of the West Coast
fisheries naturally make us cautious in accepting, without
reservation, the conclusion that the effect of the war restrictions
was an increase in the stock of plaice inhabiting the North
Sea. The natural fluctuation which, we believe, characterised
the Irish Sea during the years 1892-1920 may, quite reasonably,
be supposed to have characterised the North Sea also : it 1s to
be noted that the statistical information relative to the latter
area is very defective for the years before 1908, and between
166
that and 1914 is only a very short period. The conditions, then,
that have been observed in the North Sea are consistent with
the belief in a natural fluctuation as capable of explaining,
to a certain extent, the variability, from year to year, in the
productivity of the fishery.
“To a certain extent ” only, we may add. Probably the
Trish Sea is a more productive area, as far as plaice is concerned,
than the North Sea. The “ productivity ” depends on the
existence of the shallow-water nurseries. Just because the area
of such grounds is greater in the Irish Sea, relative to the
total area of sea, so we expect a greater production of plaice.
Probably the exploitation of the North Sea, that is, the amount
of trawling per square mile, per year, is greater than it 1s in the
Irish Sea. If that is so then the natural fluctuations that we
are assuming would be more easily noticeable in the eastern
than in the western region, particularly if, as may be assumed,
the exploitation in the North Sea is pressing closely on the
recuperative power of the nurseries.
It is quite unlikely that the data exist which would enable
us to answer the questions suggested above. ‘The fishery
statistics are too imperfect prior to 1908; the work of com-
parison of the productivity of the fishing grounds before and
immediately after the cessation of war was not thorough enough,
in any British fishing ground ; we have no available knowledge
of the extent to which military restrictions actually prevented
fishing in the various regions ;_ no detailed classification of the
‘plaice fishing grounds ” that is of much use, and, of course,
not nearly enough knowledge of the life-history of our species
of fish. It is regrettable that the opportunity for studying
the very remarkable conditions that the war-restrictions
afforded was not taken full advantage of in 1918 and 1919
by any European fishery authority.
167
BARE IV,
PRACTICAL ADMINISTRATIVE QUESTIONS.
One reason why these researches were undertaken was to
provide information that would be of use to the administrators.
It was assumed, to begin with, that there might be an
impoverishment of the Irish Sea plaice fisheries, and that
something might have to be done to arrest this. In the past
that “‘ something” has generally been a legislative restriction
or prohibition—-that is, the fishermen have been forbidden to
do this or that at one time or another and have been prosecuted
when they insisted on doing whatever was forbidden by
by-laws or statutes. Lately, the tendency has been towards
constructive administration—scientific research, the dissemina-
tion of intelligence or the promotion of schemes of development,
but so little successful has this kind of work been in England,
that it may be regarded as rather alien to the traditions (such
as they are) of fishery administration. Here, therefore, we
are obliged to suggest in what directions the results of investiga-
tion pomt—those directions being assumed to be restrictions
of one kind or other. We assume that such questions as these
are beimg discussed—the prohibition of fishing in certain
places or at certain times ; size-limits below which plaice may
not be legally captured or landed ; prohibitions or restrictions
of the operations of vessels propelled by steam or internal
combustion engines ; restrictions on the dimensions and forms
of trawl, or other kinds of nets, etc. Now a full discussion of
such measures can only be attempted when there are definite
proposals, and so we can only indicate, in the most general
kind of way, how the data summarised in this respect are to
be used. We begin with the question—/s there an impoverish-
ment of the Irish Sea plaice grounds ?
168
The Productivity of the Fisheries.
By “ productivity ” we mean the total quantity of plaice
which grow up, in a definite region, to a certain size, in a
certain period of time. It is necessary to specify the size
because it is only when the fish become so large that they
become commercially valuable, and so become commodities.
That means that the idea of productivity must necessarily
include the idea of commercial profit.
Suppose that plaice only become commercially valuable
when they have attained the size of about 20 ems., and the
age of about three years. To convert a hundredweight of
13 em. plaice into 2 ewts. of 20 em. plaice will require a certain
quantity of production in the sea and this will be much the
same as the production necessary to convert 1 ewt. of 20 em.
plaice into 2 ewts. of 25 cm. plaice. Yet the latter production
will have more commercial significance than the former quantity
because 25 cm. plaice have more value, as commodities, than
20 cm. plaice have. Production, in the scientific sense, means
the origin in the sea of plaice substance but, in the commercial
sense, it means the origin of plaice of the range of size that
sells in the markets. What the industry want is plaice of this
range of sizes and if such fish decrease in numbers the
‘“ productivity ” of a fishery region decreases.
The Rate of Exploitation.
The total quantity of plaice that are landed annually
depends not only on the productivity of the region in question,
but on the degree to which it is fished. If there is an increase
in the catching power there will generally be a corresponding
increase in the quantity of fish landed. To find whether or
not there is any change in a fishing region we require to know
whether there has been any change in the catching power
employed, and this is always a very difficult question. Plaice
are caught by steam vessels, motor boats, smacks and _half-
169
decked sailing vessels; by trawl-nets, seme-nets, stake-nets,
trammels, etc., and so we must have some idea what all this
variety of catching power means when it is reduced to a
“common denominator.” A steam trawler will catch more
fish per day than a smack and a smack will catch more than a
half-decked sailing boat. But does the steam trawler catch
more fish per unit of man-power, or per £ invested in her
maintenance than does a smack? And which rate—the rate
of catch per day, or per man, or per £ ought we to adopt ?
The ratio of steam vessels to smacks that work on a certain
fishing ground is not always the same and we cannot, usually,
neglect the fishing by half-decked sailing vessels and motor-
boats. What, then, is to be the “common denominator” ?
We may calculate how many small trawlers are equal in
catching power to one smack, and then how many smacks
equal one steam trawler. Thus we can express the catching
power in ideal vessels, or “fishing units,’ or we might try to
calculate the number of hauls made per week or day and then,
knowing the average size of the trawl-nets used, calculate the
number of square miles of sea bottom swept per day. Any
sort of calculation made in these ways would be a rough one
since we have not much exact knowledge of the conditions.
In practice, what is done is generally to calculate the average
quantities of plaice caught, per day’s absence from port, of
an average steam trawler or smack. If this decreases we say
that the productivity of the fishing grounds worked also
decreases—noting all the while that our quantity of fish
caught is fish of a certain, chosen range of sizes. Obviously
the results are rough ones in any case and too much strain
must not be put on them. Whatever changes in the results
of fishing we observe must be big enough to be much the same
(that is, to show much the same tendencies) in whatever way
we estimate the change in catching power. Thus the quantity
of plaice annually landed in England, from the North Sea
170
grounds, diminished from 1908 to 1913, and so did the average
quantity of plaice caught per day’s absence from port of the
average steam trawler.
Of course the whole question is a rather academic one :
what the owner of a steam trawler has to consider is the
average cost of catching the average cwt. of fish and then the
average price obtained when it is sold.
The Impoverishment of a Fishery Region.
For the moment we deal with plaice of a definite range
of size—say, 20 to 25 cms. (small plaice). Suppose that the
productivity of a certain fishing region is “ indefinitely great,”
no matter how many plaice are caught there would still be
plenty left—that would be what we mean by “ indefinitely
great.” So many small plaice are produced that a certain
fraction must die from want of food: now if, say, 1/LOth are
caught by the fishermen that would mean that about the
same number would not die, but would survive to take the
place of those that had been caught. Probably some localised
fishing regions are like this—they are “‘ overcrowded ”’ grounds.
On the whole, however, such an area as the Irish Sea is not
an overcrowded one, where the productivity is indefinitely
ereat, for the fact that the abundance of plaice undergoes
periodic changes shows ether that the quantity of plaice food
changes, or that the quantity of baby plaice spawned, hatched,
and transformed changes. Probably the latter is the case.
Has there been an Impoverishment of the Irish Sea Plaice
Grounds ?
To answer this question we have to consider both the
commercial statistics and the results of experimental trawlings.
The quantity of plaice landed from year to year depends on
the catching power and the natural productivity of the grounds.
The statistics of catching power are not very accessible (if they
exist), but it is probably the case that it has not decreased
171
of late (except during the war years). The number of steam
vessels working from Fleetwood has increased, and though
most of these vessels fish outside the Irish Sea region it is
likely that much about the same fraction of all of them trawl
on these grounds each year. The number of smacks working
from Fleetwood and Hoylake has steadily decreased since about
1890, and there are no indications that the number of half-
decked sailing boats has increased. But the increase in
number of the steamers probably makes up for the decrease
in the smacks and the decrease (“if any ’’) in the small boats.
Probably, then, the catching power is approximately uniform
or has increased.
So far as the commercial statistics go they show that
there are marked ups and downs in the quantities of plaice
landed from the Irish Sea. There was a maximum in 1911,
a minimum about 1915, and another maximum about 1920.
Thus there is no definite tendency one way or the other, so
far as these data enable us to discuss the question.
So far as the experimental trawlings go the same conclusion
is to be made. There are ups and downs, and these are nearly
the same as the changes revealed by the commercial statistics.
In fact these two series of data support each other to a certain
extent and indicate that there have been actual changes in the
natural productivity of the Irish Sea grounds during the period
1908-1920.
When we deal with the measurements of lengths of plaice
caught on the fishing vessels (steamers and smacks) and caught
experimentally there is rather more trouble, because there are
so many ways of going wrong in our deductions. “* Lumping ”’
of the various grounds in even such a small region as the Irish
Sea is fatal. In the winter of 1920, for instance, a fairly large
number of plaice were measured on the Solway grounds and
these were all rather small fish (see Tables 26, 27). Also
2,275 plaice were measured on board a steam trawler working
172
just outside the territorial limits in Liverpool Bay (Col. 1 of
Table 26), and these fish also were unusually small. Now
these grounds were not worked in the corresponding months of
any of the previous years, and so (just because of this difference
in the sampling methods) the size of plaice on the “‘ North-west
Coast region”? would have appeared to have diminished in
1920 as compared with previous years. Therefore we must
distinguish, to a rather fine degree, between the various grounds,
and we must compare, with each other, only rather small areas.
Kven then there are “accidental” variations that might
mislead us. Thus a good breeze of wind may make a
perceptible difference in the kind of plaice found on a ground
in the course of a few days. We have seen, however,
that it is not the difference in the rate of growth that
makes the fish on a ground appear to be bigger in some
years than in others, but rather the varying proportions of
older and younger plaice. That means, then, that more fish
are spawned, transformed, and reared (one or all) in some
years than in others, which means, again, that some years are
more productive than others. So there is a good deal to be
made out of the length measurements—if we are critical.
If only we had had good series of plaice measurements in 1889
(when the regulation began in Lancashire) the questions pro-
pounded now would have been more easily answered. Perhaps
this is the most convincing argument for the future utility of
the series of measurements recorded in this report.
Is there an “ Accumulated Stock” ? Does Increased Fishing
tend to make the Fish run smaller ?
An “accumulated stock” of plaice means that the fish
grow old more rapidly than they are caught. There is no
accumulated stock in Liverpool Bay because the plaice migrate
out from this region as they grow old. But even if the natural
conditions were such that plaice of five or more years of age
173
preferred to remain in Liverpool Bay they would probably
not be any more numerous than they are at present. There
are fewer fish of six years old than there are of five, fewer of
five than there are of four, and so on, and therefore trawling
affects the abundance of larger fish more than it affects that of
the smaller ones. There is so much trawling in Liverpool Bay
that the abundance of these larger fish would be kept down,
even if the grounds were natural ones for such plaice.
On the other hand we do seem to have an accumulated
stock of plaice in Luce Bay. We have reasons for believing
that fish that have spawned on the northern grounds migrate
into the Bay when they become spent. They are protected
there because trawling is effectively prohibited by the Fishery
Board for Scotland, and the other methods of fishing that are
practised are probably quite insufficient to bring down the
numbers of the big plaice (up to 65 cms.) that are found there.
Did a Stock of Large Plaice accumulate in the Irish Sea during
the War Years ?
We have discussed this question in the preceding pages
and find that there is no very good evidence that such an
accumulation took place.
Our conclusion is, therefore, that there is no reliable
evidence in favour of the conclusion that there is an impoverish-
ment of the plaice grounds of the Irish Sea due to over-fishing.
But it may be said that the plaice there “run rather small”
and that they might get bigger and so become commercially
more valuable if there were size-limits, or restrictions of other
kinds. This further question must briefly be considered. If
We could, by any means, raise the prevalent size of plaice from
(say) 23 to 30 ems. the same total weight of fish landed would
be more valuable. If, further, we could so legislate that the
same numbers of plaice would continue to be caught, but that
174
the prevalent size of these fish would be 30 instead of 25 cms.,
the fisheries would become still more valuable. Apparently
it is some such ideas that are at the bottom of any suggestions
for size-limits, ete.
The Possible Effects of Legislative Restrictions.
The only kinds of restrictions or prohibitions that seem
b)
to be “ practical politics” are (1) the closure of spawning, or
nursery grounds, and (2) the imposition of size-limits. One
may ask, first of all, whether it is practicable to enforce such
restrictions or prohibitions. Of course this is no business of a
scientific investigator any more than it is the business of the
Central Authority (which has, of course, no power of actual
fishery regulation, but is only responsible for the approving,
or initiation, of policies). Still the whole affair, that is, the
initiation, approval, and enforcement of legislative proposals,
ought to be one, and any person that recommends a policy
ought to be prepared to consider whether or not it is practicable.
He ought also to consider in what way it is going to affect
the existing fishery customs and populations. It must be said
that a fair amount of actual contact with the fishermen of this
coast, and some experience of the difficulty and enforcing highly
unpopular restrictions does not encourage us to regard anything
of the kind with much favour.
The Protection of the Spawning Grounds.
Should we add significantly to the number of marketably
valuable plaice in the Irish Sea by preventing the capture of
spawning fish on the Solway grounds? Any measure of this
nature would mean the closure of a fairly well-defined area,
and the employment, therefore, of an efficient police. It is,
further, an “international” question since the area is mostly
outside territorial waters. We are not certain, in any Case,
that it is the eggs and larvee of the plaice, in the Irish Sea, that
175
ought to be protected should we have to admit that there 1s
progressive improvement of the grounds. Evidently, then, this
question need not be further discussed in the meantime.
The Question of Srze-linuts.
First of all one asks how any specified size-limit would
affect the various classes of fishermen on this coast, and what
is to be the size-limit? Those that have generally been
discussed are 20 and 22 ems. (8 and 8? inches). Such a
restriction would mean that a certain fraction of all the plaice
caught by the inshore trawlers (the few smacks, the half-
decked sailing vessels and the stake-net fishermen) would have
to be returned to the sea. The length-frequency distributions
tabulated in this report for the various areas and seasons enable
us to state approximately what this fraction of rejected plaice
would be. If the limit were 20 cms.—and still more if it were
22 cms.—the fraction would be so great that the restriction
would interfere, in a most serious degree, with inshore fishing
on the North-western Coasts. It would be most strongly
resisted by a class of fishermen who are, by no means,
inarticulate. The question, however, may be deferred until
definite proposals have been made.
How would it affect the Smacks and Steam Vessels ?
There are now so few smacks left that the question has
little significance (except for the few smacksmen, of course).
At any rate the Imish Sea smacks fish in the summer mostly
for soles, and small plaice on the sole grounds are not very
numerous. >| 83S g >| 3S * el aN
parents We Ps Bo lat lee ee
mH |a4o]8 mS |4O/8 mH |}qO|¢g
= 3 3
N a) 2)
0:095 | 0-199 0°34 | 0:98 0-027 | 0-067
Hee 0°785 0°57 0-000
14 0-000 0-000 0-000
Taste I1I.—Calculation of P on bulk samples of Welsh herrings.
Winter, 1913
Winter, 1914
CHARACTER D.
CHARACTER JV,
CHARACTER L.cp.l.
| Winter,
1914.
Winter,
1921.
0-000 0-000
weet eet wees
0-000
seers eee eeee
Winter, | Winter,
1914. 1921.
0-000 0-9
0-000
Winter, | Winter,
1914. 1921.
0-000 0:05
0-000
TaBLtE IV.—Calculation of P on bulk samples of trawled
herrings from the Smalls.
October, 1913
CHARACTER D.
October, 1914.
0-00008
Peer trees eeeee
CHARACTER J.
October, 1914.
0:0008
CHARACTER L.cp.l.
October, 1914.
0-099
188
Dealing first with the small sub-samples of Manx herrings
taken during 1914 (Table I), the general result based on
character D supports the view that the differences are most
likely due to errors of random sampling, except in the two cases
where June 3rd is compared with June 13th, and June 13th
with June 25th. In these two cases the odds against the
differences being due to random sampling are 333 to 1 and 19
to 1. In all the other cases they are less than 10 to 1.
Comparing these results calculated on D with results
calculated on lcp.l., we find confusing discrepancies. The
lowest odds against the differences being due to random sampling
are about 14 to 1, in the case of June 25th compared with
July 9th. This is becoming unsatisfactory; and they even
become as high as 1,000 to 1 when June 3rd is compared with
June 13th. So that, with the exception of June 3rd and
June 13th, the result based on character D is negatived by
that calculated on l.ep.l.
The lumped samples are next compared (Table ITI) and the
three characters, D, V, and l.cp.l. taken. Only in one case
out of four, the summer season of 1914 compared with the
summer season of 1920, do we get agreement on all three
characters, the odds against the differences bemg due to random
sampling being more than 1,000 to 1, as computed on each of
the three characters.
In the other three examples D and V show odds of 10 to 1
or less against the differences being due to random sampling,
yet l.cp.l. shows these odds to be so increased that they are
either in the region of doubt or improbability.
The examination of the Welsh herrings (Table III) reveals
a high probability that the differences are due to reasons other
than random sampling. But one confusing result occurs which
is unexplained. Winter 1913 compared with Winter 1921—
character V gives odds of 1-1 to 1 against the differences bemg
due to random sampling. On l.cp,.!, for these same samples
189
the odds against are 20 to 1, and on D over 1,000 to 1. The
samples of Winter 1914 compared with those of 1921 agree on
all three characters, with odds of more than 1,000 to 1 against
the differences being due to random sampling.
The trawled herrings from the Smalls (Table 1V)—October
1913 compared with October 1914—show somewhat conflicting
results. D and V suggest that the differences are due to
causes other than random sampling, but l.cp.l. shows much
lower odds against—about 10 to 1—whereas in the other two
cases the odds are over 1,000 to 1 agaist.
It is difficult to explain these anomalies. We consider
the most reliable character to be /.cp.l. from the measurer’s
point of view and would regard it with more confidence perhaps
than any other character. It is clearly defined and does not
suffer from the effects of distortion due to bad. condition,
freezing or softening, as might D, V, or A, and in nearly all
cases P, when calculated on this character is low. In the one
case only—that of the Smalls, October 1913 and October 1914,
does this character give any value of P which indicates any
approach to a “ good fit.” So that the bulk of the evidence
inclines to the theory that there is no racial homogeneity in the
samples compared.
It seems pretty clear that the herrings inhabiting the
Irish Sea are a mixture of sub-races, or genotypes, and
that one of these predominates at one time, and another at
another time. For the chances that the differences observed are
due solely to errors of random sampling are, very often, far too
smal! to allow of any other conclusion. Further complications
are the choice of the diagnostic character, or whether we should
not, preferably, choose a combination of characters, or whether
some other character than those studied must be sought ?
Evidently the question of races is not so simple a one as has been
thought and some further investigations, as to what characters
are truly germinal ones and what are environmental only, must
190
obviously be undertaken. Meanwhile we hope that the
records given in the frequency distributions may serve for
comparison with other sea-areas.
The possibilities of a shifting with growth of any one of the
characters investigated should also be considered. That this
actually happens in the case at any rate of young herrings of
from 30 mm. to 60 mm. is very clearly shown in Table V.
This is a series of measurements of young herrings from North
Wales made by Mr. Andrew Scott and examined by Professor
Johnstone. The distance D is expressed as a percentage of
T (total length) and correlated with 7 as tabulated, giving a
coefficient of correlation of —0-9696. This is almost absolute
correlation. The form of the table shows at a glance how the
dorsal fin is gradually moving forward as the young herring
is growing.
This investigation of the shifting of characters was
extended to the sprat. Measurements were made by Mr. Scott
and tabulated by Professor Johnstone. Tables VI and VII
show the results. Table VI is a correlation between the
position of the dorsal fin and the total length. The result
shows that this character does not vary in any regular way with
imcreasing length. Table VII is a correlation between the
position of the ventral fins and total length. This shows a
somewhat irregular tendency to move forward as the fish grows,
but not so definite as in the case of the dorsal fin of the young
herring.
Unfortunately, in the case of the samples of larger herrings
examined by us, time did not permit of more than four
correlations being made. Three of these were based on
character A, and one on character D. The results were
inconclusive, as Tables VIII to XI show. There is little or no
evidence of correlation in any case investigated.
191
TaBLE V.—Correlation between length and position of the
dorsal fin in the Herring.
Total
length.
31-33
34-36
37-39
40-42
43-45
46-48
49-51
52-54
55-57
Distance of dorsal fin from snout: °%
Totals |
/O
ae Es Totals.
43-44 45-46 47-48 49-50 51-52 53-54
EY aa fe ee ee
1 Ph) el 24
a00 isle an 9 42 8 59
Sas “ies 1 3 33 1 58
She 3 5 22 1 F 31
1 7 19 1 28
4 22 2 28
1 4 1 6
4 6 ae 10
ioe ese s6 | 79 «| «631 || ae
r = Coefficient of Correlation = — 0°9696 + 0:0005
TasLe VI.—Correlation between length and position of the
dorsal fin in the Sprat.
Distance of dorsal fin from snout: % |
Total | Totals.
Length. =
41-42 43-44 45-46 47-48 | 49-50
30- 49 4 37 106 45 12 204
50- 69 anc 17 100 77 18 212
70- 89 14 90 83 12 199
90-109 as 12 154 99 4 269
110-129 3 a 73 U 380 90
130-149 see ae 9 5 ee 14
Totals ...... Tease acne eicn es), 460 <|) tose.
r = Coefficient of Correlation = — 0:0945 + 0°0205.
TasLe VII.—Correlation between length and position of
the pelvic fins in the Sprat.
| Distance of pelvic fins from snout: %.
Total
Length. i
40-41 42-43 44-45 46-47 48-49
30- 49 1 8 107 62 19
50- 69 3 46 97 46 9 |
70- 89 10 79 84 24 6
90-109 2 109 148 8
110-129 1 47 40 2 |
130-149 4 5 4 3. |
Totals ...... 21 294 480 142 34 |
r = Coefficient of Correlation = — 0°5005 + 0-015,
| Totals.
192
TaBLe VIIT.—Manx Herrings, 1914. Character D.
Correlation between T7'.cd. and D expressed as a % of T.cd.
Be :
48— | 49— | 50— | 51— | 52— | 53— | 54— | Totals. || Means.
48:9 | 49°9 | 50-9 | 51-9 | 52°9 | 53-9 | 54:9 |
|
|
| |
180-189 onc 200 1 Zia wl Alen are 17 | 52°44
2
=
23) 190-199 | ... |... A> |. 35 6:10 3 67 5225
g 3 200-209 ie 3 27 58 fil |) Uy 3 159 51°88
a8 210-219 |... 2 38 96 1 | 47 3 228 ~=||:«#51°82
EE 220-229 1 1 19 45 44 27 3 140 || 52-09
8 B+ 930-239 |... Gs 6 15 17 | 9 2 49 | 52-21
Hale AQ E40 a zee dle ole meen eel eee 32. feelers 3 || 52°50
2 |——— | | a
| & | Totals ...... 1 6 | 95 | 243 | 219 | 85 | 14 | 663 ||
r= eee , Si See
= (Means ...... 225 | 211-6 | 214-26| 213-15 213:40) 214-18] 213-57
, = Gaomoens of Goren - 0:000499.
TaBLE [X.-—Welsh Herrings, 1914. Character A.
Correlation between T.cd. and A expressed as a % of T.cd.
| |
| 73— | 74— | 75— | 76— | 77— | 78— | 79- |
73°9 | 74:9 | 75°9 | 76°9 | 77:9 | 78:9 | 79:9 | Totals. || Means.
|
fo. 1802189 | jhe SoC an eeLGo, MO Cranes 35 | 75°78
= 190-199 | 4) 2 eG | aels es ae 45 || 75°50
2 200-209 | 0 4], 4a ise ide a 1 29 || 76-26
5 10-310 |) 25. Phar aaa cies (ele eT 1 | 47 Neos
B's) 920.090 | 1 | a oe ape ns |e 85 || 76-38
Be) 2° 6280-280) 2.7 | 3 BE il UT Ga 2 | ei) Rome mnee
Feil G20 249.011 sw 1 cecenn ae gea el ee a 4 | 76-00
5B | Totals...... 6 || 86 (See 550 ieace ein i ere
oO
=
| Means Bence 201°6 | 205-1 | 209°5 | 215°7 |216°7 | 218 215 |
| |
r = Coefficient of Correlation = 0-267 (-+ 0°047).
Actual measurement of T.cd.
Actual measurement
of T.cd.
193
Taste X.—Welsh Herrings, Winter, 1921.
Correlation between 7.cd. and A expressed as a % of T.cd.
/O
Seas ste fs tk! era |
Rees tae TG Tr 1 7T8— Wo |80
| 739 | 749 | 759 769 | 77-9 | 789 | 79:9 | 80-9 | Totals. | Means.
| | | | | |
190-189 | ... ; 1 | i | Poe ttel a en ee ya lve 27 77°50
190-199 | 1 | 1 ey Ole Tome dae MON Or Nace enna
200-209 | 1 | 1 | 3 SS) eae) 4 55 «| «77°50
| 210-219 | Meeec5oe abt |) t15, 6 | 4 42 | 77:26
220-229 | re ad) | ekO}. aed 2 19 | 77°76
230-239 | 2 fs\tOnt |) 12 ] 29. aaa
J BE a ee ree 2 5 7 ler afi aoe NTS:06
250-259 |... Te eee hy ss, i i ere re feet am 76:00
SOCOM Pei liicee! | ce || psn: ee eee 75°50
Totals ...... 25) 5 13) 950%), (997 | 60 | 18 1 | 248
Means ...... 200 | 211 | 210-38' 207 | 210-15 214-3 |211-11) 195
| | |
r = Coefficient of Correlation = 0-094,
Taste X1.—Manx Herrings, June, July, August, 1914/20.
Correlation between T.cd. and A expressed as a % of T.cd.
| | ]
tlre lis aie ain renee (|e. Ps ;
| 73— | 74— | Jo— | 76— | 77 — | 78— | 79— | 80—
73:9 | 74:9 75:9 | 769 | 77:9 | 78:9 | 79°9 | 80-9 | Totals. || Means.
: | gee
Ge EOAWTOn Wala. leva ||, fl ys 1 (il cere tee Bl) aavelley
TSGstO glee) 26 Se] “4G 6 Saas | 1 | 25 76°54
RAO OOM 2p 12 NES esis soe 4 |) 2) 2 | 188 76°65
200-209 | 3 19 | 46 68 46 30 6. i 2 220) ||) We:59
210-219 | 2 | 13 | 33 | 55 46 \4 a || | 170 || 76:68
J 220-229 .. | 1 | 10 | 14 | 29 | 15 4 | 74 Ts
230-239 1 meee 3 7 3 2 17 77°68
| Loe en ee ee
Rotalees-s aS | aol lly welss eT |, 80 * |) 21 7 | 642
| | ad
| Means....... 208°75 203°24 206°32 207-35, 209-33) 208-75) 214-05 206-43 |
r = Coefficient of Correlation = 0°152.
194
REMARKS.
The mathematical investigation of these data can scarcely
be regarded as giving very satisfactory results ; many of them
are conflicting and in some cases one result completely annuls
another. The reasons may be sought in many directions, some
of which under present circumstances would be difficult to follow.
We might get more trustworthy results from weekly samples
of herrings and by dealing with them immediately. This,
however, would necessitate the abandonment of some other
equally important work during a very critical time in a marine
laboratory programme. Methods of measurement might be
improved and additional characters investigated, including the
counting of the vertebrae.
The grouping of the data according to scale markings has
been considered. That is, instead of giving a range of per-
centages of T.cd. of any one character and lumping together
all the fish of a sample irrespective of their ages, as we have done
in the present report, the fish would be selected according to the
scale markings and each age group treated separately. This,
however, has the great disadvantage of reducing the present
dats. to many groups with much smaller frequencies and would
consequently necessitate much larger samples. The samples
would at least be homogeneous as far as age was concerned, and
any peculiarities due to a possible shifting of any character
might reasonably be expected to be confined to the particular
age group under consideration and to be evenly distributed
among the varying length frequencies.
Our examination of scale markings of the various samples
considered reveals great heterogeneity as regards age. A sample
generally contains fish with from two to six scale rings. In
some cases one special ring group will predominate, in another
perhaps three groups will be equally represented and form the
bulk of the sample.
195
We do not consider the keeled scales (K,) to have any
particular significance and they seem to show very little
variation. For this reason we have not investigated them
mathematically.
Our indebtedness to Professor Johnstone is acknowledged.
He drew up this scheme of investigation and supervised its
carrying out. Thanks are also due to Mr. Smith and
Mr. Fleming, who have helped in the measuring and examin-
ation of all the samples. It should not be overlooked that the
measuring and examination alone of a sample of 50 fish is a full
day’s work for two operators, and the greatest care must be
exercised. Scale reading takes up a great deal of time and
becomes very trying. The results of scale readings of the
samples will be the subject of another report.
The analysis of all samples received from the commence-
ment of these biometric investigations in 1913 to the present
time are appended. See Tables XII to XX.
“Range” of a character im the Tables means the per-
centage of the measurement 7’ cd. occupied by the measurement
of the character under consideration. The material is divided
into sub-samples, which appear under the heading of locality,
month and year. The final column for each year is the total of
these sub-samples and forms the * lumped ” samples data.
Table XX. Character K,. The “range ” of these data
are not percentages of T.cd. but absolute numbers of the
keeled scales as counted.
TABLE ex):
196
Range of D.
46°00
46°25
46°50
46°75
47°00
47°25
47°50
47°75
48°00
48°25
48°50
48°75
49°00
49°25
49°50
49°75
50°00
50°25
50°50
50°75
51:00
Dd;
51°50
61-75
52-00
62°25
52°50
52°75
93°00
53°25
53°50
SAEED
54:00
54°25
54°50
54:75
55°00
55°25
55°50
55°75
bot
~
=
—
On one a)
—_
Ne = oc ©
WwWwods
ae
+ oo
— —
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be | oe
s. |<
a | 8
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= | & |
5
ell OO Od
re
et
~ . . . .
2 | Sapsaeales ie 2
Wee es] eS cea I et
o (on) — — ia! ea (=>)
— “ n~ n” Cy —/
jos Ss Oo © or) a n
| 3 Sal Tetest ape maker liege acs
" = - ol a a
4#iS S/8is la is
< fa i — — = x
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—
=
!
| i l
|
» G3
res ea
1 1
|
| |
| |
eee leas
| 5 | i 1 eee | 2
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| | il 1
2s 5 1 |
4 I gaan |
Bot [reDea
5
5 |
|
|
—_
ae?
a et SO OS DS 01 GS OS Tb bb:
ees
> et OU SUIS OH Ge SD GS
RWW RUA WTIR eo:
Or
ye
—.
—
-I
—
bo:
ars
Eat
eee bobby:
mT O10:
Manx, 3, 1921.
Manx, 5, 1921.
ee On
We PRUIKROWwW oP BP:
Manx, 8, 1921.
Manx, 1921
es
—_
as
w
to
—_—
bo se we
mee OOHRS e:
—
be
328 190
|
i
149 667
| |
60 |153 | 60 [181 454 |
|
49
24 |120
(PABEE OP — 7)!
. me = a al . .
5 Reals ce ees eee esi le Ss
a =r) fon] | Co inn =r) =r)
S oa) eels at as = a z
S st | rm i . en & cy
i ae fe Sh ee ee
| eo { =
48-00
48:25
48°50 ee
48°75 rs Ee l + i: | Ae cet
49-00 oe Poca (Rohe a er Be 63 l
49°25 1 3 1 1 ay ae
49°50 2 4 1 | |
49°75 | 5 oe oY a 2
50-00 4 26 2 Sa | 3 vr 4
50°25 eer, 26 1 I 2 l
50°50 9 20 4 l 5 2 se
50°75 aniiee oll 4 2 6 2 4
51:00 10 in eens 1 2 16 5 i
51-25 21 33 13 6 | 20 5 9
51-50 15 34 19 4 2: els
51°75 10 Waele y| 1 25 5 9
52-00 10 19 17 2 a 19 ia 12
92°25 15 20 17 7 I 25 12 18
92°50 10 11 21 9 5 35 11 11
52°75 3 4 10 4 1 15 17 5
53-00 on 3 15 Gil 33 19 8
58 5) 5 6 5 4 15 12 ll
53°50 l i 5 2 14 14 2
53°75 4 5 4 9 7 2
54:00 3 l 4 9 13 12 1
4-25 4 2 6 2 1
54°50 1 2 5 7 2 l
54°75 2 2 2
55°00 1 L 2 ns
55°25 3 3 2
55°50 | l
55°75 ie I I 2
56°00
56°25
56°50 | |
56°75
57-00
141 | 280 | 185 | 61 | 48 | 294 | 150 120
| | (eerteslea Eos § mul
|
|
198
TABLE XIV.—YV.
“i _ | | | |
. Pe ss. eee
= ealal~lS eiSl/Sl(SlalSlalSja
B ele Hal) al een ee eo ay fo) SS
= S eh st a) Se ec los | o> | -. | oS | am |) od =
Et) ~ ~ oS w : . o o ial * a * Last
PI 4 mn S va | ee hy IER || %S 4 4 4} <4
a\e| 4 lz \/Slelel"\s\sis
| = | | |
48-00 me i i
48°25 a oe 25
48°50 i 1 1
48°75 ay ata 2
49-00 pe Seale | 1
49°25 wi eh pe 1 j
49°50 BY wales. oe »
49°75 ee el ee 1 ;
50°00 es eae * | os -
50°25 EN, [ek Weer Meee at me
50°50 eb ee Oe lt elie Ey
50°75 SU ean ee a | eats aa
51-00 LO bie poet ee ota | es 4d,
51:25 TWAS Deed Wee | (ea fae ca Pe en Salven a
51°50 iia feces | a | ee fc Ly eee eat 1
51°75 Tea eee eon) Fa, Pet 1 eee |e we
52-00 xecep l|eB | gel mee a cx ea eee | ee alien: shan! ah
52°25 1) se Re a a eT: Sul eerie
52°50 BF NMR eR OT ea a een ta a
52°75 Beetles el Sa Oana S| a OST al) ees eee sn
53°00 Gileaal eetaliaia OSS Fay 2 6) ca |e | eee
53°25 19)! VEU ga eos) el 7 oe Oe
53°50 184) 2-83) 8-949) Sel 104) 24 ee) ea) ee
53°75 9g 19) V4.1 549) “3°! 10°) 6 | 2.) 18 |) eae
54:00 59 90) ieee) 2 18)| 7) eo | ee ee
54°25 Deal a0) | 8s, 46.) 16-110) 4 | 98. 29.1) Se ee
54°50 99 | Ist 53.) 27] 19) 8 | “70)-96'| “Ue oueeo alee
54°75 99 | 17 19)| 51) 4113) 41) 95 96) Sona
55°00 41| Sesh isst | 6 112) 7 SSG) 65 aire ails
55°25 99°) Fo 11 145 | 6 | 4) 62°) 1071214) 35) on ea ee
55°50 F716 Ti | 54.) 4) 6" V4) 16 eS ee ee
55°75 16) 12.) 7 35) 41 Sel 1 1 20 NS eee ieee
56-00 Wl 2) 8199! 11 -6-| 1) 10s) Tse) ey eee
56°25 13°) 8 17 1-28)| ea) 3), 22172031295 4) Ga eee eaten
56°50 7) Oil 4407) | 2.) 25 eGelaa a So ee ee
56°75 Bi) oO Sa) Ft) 3c Seas eas ee ee | eee
57-00 Tie Peso | Om feta eee 197 1G | il eee 2
57°25 Soul soul. ill well 14 IS ee o 2
57°50 Same loreal 73) wl al cred 16 aN oe nl
57°75 id | ocr hay 2D ibe ee al nasa ool 1
58-00 aul 3a 7 haley |e 1
58°25 l ee ee ate 1
58°50 ot a Nae | Oe ee a
58°75 ae 5| 5 ee
59-00 Real 2| 3
60-00 1 i lee
61-00 Kees feed l
329 |190 [149 [668 60 [152 | 61 es fe | 47 | 49 | 24 |120
a
199
TABLE XV.
—V.
“s eee fe | ae ah Ss See
: ee eo | ae lean
8 mee le oe oe
a = = Se | Sa a &
48-00 | | | |
48°25 |
48°50 ee: |
48°75 nee
49-00 aft
49°25 | ies
49°50 | Whee :
49°75 tp ee 355 | |
50-00 | eee leecale | |
50°25 f a. Wenn sae |||
50°50 a ” pant le |
50°75 tes ne roe Be
51-00 1 ee lesen ey ‘
51-25 1 St | i oo
51°50 a 1 | ian vs
51°75 in a ee |p ae if aes
52-00 ae Me ye ie ey ih Bele wa I
52°25 ee 9 ce cit we a | hee 1
52°50 i 4 - 1 TEP ea | eee es
52°75 a | ae 7 1 3 Sei) Geile Bae wis
53-00 2 i 9 4 5 os Oliva: 2
53-25 4 16 4 1 a Bat 5
53°50 6 18 8 1 De LS ee 4
53°75 2 28 9 2 a Tia Ble at 5
54-00 5 25 8 4 Pe aioe es 8
54°25 9 29 10 ll 7) 95" les 5
54°50 11 28 15 6 se 21 || 10 12
54°75 16 | 29 19 4 1 24 || 17 12
55°00 13 19 15 8 1 94 | i 13
5525 15 28 28 6 2 360 |) 10; ol 28
55°50 11 7 11 Pala esi ae) 1) a
55°75 11 11 13 3 2 189) Pero 4
56-00 9 3 10 aw 6 16 || 10 15
56°25 7 2 | 15 3 4 22 || 6 7
san! 9 Bee | sat l 3 ae ny)
56°75 2 eo 4 9 | 9 n
57:00 1 ees | 9 Gers l
57°25 2 (Pao 6 8 5 1
57°50 Dees late 1 ee Te hoes ee
BT15 Pi ike Al) ed eee Doli ately.
58-00 1 cee are ane eee oe |
58°25 ae fl 2 Be Wetec
142 | 285 | 183 | 61 | 49 | 293 || 149 - 120
| }
TABLE
: ~}al/afi/ai/= oilbhS Smile Ite Pe | aial|.
x i eee | os. see Meal es Sree. Meee cee- | ped Ges | uoeal lees
oo | el tl 4 3 2 ee a head = =— = | = =
r= 4 | K SO Ela ee || si eh || iz 4 A 8 wo | al |e
CI ea |< i ash |i 2 oF a | 8 I et Wek i) Siti ics
pe E a@i\e/e|/e|a| s | S |S) See lS Se slae
yt ee eee a vee aes = a S| = ee re
|
73°00 1 il
Hetedse Ae heal ees Be s&
73°50 | 1 feat | Sah 2 a
WOT Bs | wae | leer [lee 2 3 he
74:00 | Sale 4| 2 4 6 | ules
74:25. | 2.| ... 2 | 7 8 1
74:50 | 4-|. 1 | 3. | 5 3 6 9
FAs | eecst) 6 | oh erie 3 8 11
TsO en ele loge bbe se) 2H it 9 163) ese =i
Tips | eS ale ell ese) eee sl meen ALS 1 VB | sell ce ce LGM ean cere
75°50 eae lea meat ree nea | 12 Bh. Gy) AG a eas
7576+ | 151.971 3) eas 1) 29 3 6 1 TOmh oo ee 4
76-00 $1.10] 5| 1] 31/27 3 14 AAR eae 44 Wal eee aes
16200) L6s\= 9) 42) 2a 43> 5 9 AL | GY | Bl Di} Al &
76:50 | 17 | 14}... | 3 | 1) 35 6 16 Dit isce al dar|) V2 aell Cea
76°75. | 21:),100) } o
cl ion)
: 5
2/8
PLS ore
sot 3
: 3
6
8
10
S06 13
3 23
2 29
1 25
1 36
5 29
4 | 2
3 15
10 22 |
7 19
5 16
3 4 -|
4 8
1 2
30C 1
49 | 294
Smalls, 1913.
| 150
Smalls, 1914.
| 119
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205
SEASONAL CHANGES IN THE CHEMICAL
COMPOSITION OF THE MUSSEL (MYTILUS EDULIs).
(Continued).
Bye). DANTEL, B.Sc:
The investigation into the seasonal variations in the flesh
of Mytilus edulis, which was referred to in last year’s Report on
the Lancashire Sea Fisheries Laboratory, has now been con-
cluded, and covers a period of two years. Observations show
a marked annual reproductive cycle which, on the whole,
repeats itself in each of the two years. The discrepancies are
probably due, in the main, to the unavoidable errors of
sampling.
The data obtained from examination of the samples,
tabulated in various ways, 1s shown in the attached tables.
It is not possible just yet to publish the results obtained from
microscopic sections, stained to show the distribution of fat and
glycogen in the tissue, but since the information obtained from
these latter investigations is closely bound up with the fluc-
tuations in chemical composition, it will be necessary to refer
to it im passing,
The samples sent from Morecambe are to some extent
selected ” mussels. They have been gathered in the same
manner as the fishermen pick them for food, only those greater
than two inches (5-1 ems.) being taken. This is not altogether
a disadvantage ; it lessened the irregularities with regard to the
_size of the mussels, and allows of results which are comparable
with the shellfish that are actually put on to the market.
Most of the mussel samples showed an average length of
6-0—6-5 ems., and only five of them averaged so low as
5:5—6-0 ems. There were one or two samples which were
obviously not in the “ general” run. For example, the mussels
received on August 16th, 1921, were small, and with very
dark shells ; they were procured from a bed near to Morecambe,
and not from the usual Skears. On the other hand, the
206
sample for December 17th, 1920, was composed of mussels so
large and well-nourished that they must have enjoyed the most
favourable conditions on the Skear, from which they were
obtaimed. Although such samples cause irregularities in the
tables showing weights and percentages, they do not obscure
the general trend of the figures.
The methods of dealing with the shellfish in the laboratory
have already been described.* The selection of six mussels at
random from the whole sample, for the drying and subsequent
analyses, has been successful, within limits, as may be seen by
examination of Table I. The figures for the average weights
of shell and of flesh for the six mussels, and the corresponding
ones for the rest of the sample, do not show differences which
alter the main conclusions. For instance, a graph plotted for
the average weights of wet flesh for the rest of the sample
shows fluctuations, but the curve does not differ fundamentally
from a corresponding curve for the six mussels.
Differences in Weight.
The weight of wet flesh in both years rises from May,
with variations, to December, and then maintains a relatively
high value until there is a rapid fall to almost half the maximal
value in the April 01 May of the following year.
The series of weights given by the dried flesh show the
same sequence in a more marked manner. It will be seen that,
during one part of the year, it is possible for the mussel beds to
yield two-fold the amount of foodstuff that they offer at
another time.
The proportion of water to dry flesh is least from August
to October, and shows an increase before and after spawning in
the Spring. There is no doubt that all these differences of
condition are connected directly with the reproductive cycle of
Mytilus. In May the mussels were in a spent condition. The
* Report on the Lancashire Sea Fisheries Laboratory, 1920, pp. 74-84.
207
reproductive products, which invade and cause to swell enor-
mously the mantle, and also every part of the body which is not
occupied by organs or muscle, had been extruded, leaving
behind a thin, watery, and semi-transparent animal, so
emaciated in appearance in the case of the older mussels that one
is almost led to wonder how they survive. The “fat”
condition of the molluse which forms such a contrast to this
state of emaciation, is dependent upon the amount and
conditions of the sexual products ; this is ‘‘ common” know-
ledge to the fisherman, and a closer examination of the
reproductive phases during the two years under consideration
bears it out.
The spawning time of the mussels in the Morecambe Bay
area has received some attention in the past. Herdman and
Scott* record that in 1894, mussels matured about the middle
of May and that spawning continued until the middle of July.
Scott} confirms, two years later, that the mussel reaches
maturity about the middle of May. So far as the Morecambe
Skears themselves are concerned, Mr. Edward Gardner,
Honorary Bailiff to the Lancashire and Western Sea Fisheries,
has kindly given information drawn from his long experience,
and which may be summarised as follows :—The main spawning
time is about the middle of April, but the actual date varies
shghtly according to the weather. Some beds seem to ripen
before others, and there may be a spawning at the back end of
the year which never comes to very much and seems to be
due to the younger mussels which recovery more rapidly than
the older ones.
Certainly there is other evidence for this spawning later in
the year,t but so far as the evidence of the two years under
* Herdman and Scott. Lancashire Sea Fisheries Laboratory Report,
1894, p. 40.
ft Scott. ibid., 1896, p. 5.
+ Johnstone, Lancashire Sea Fisheries Lab. Report, 1898, p. 36;
Ascroft, ibid., p. 81.
208
consideration goes, if was centred round the month of April.
The fall in weight in the October and November of both
years might suggest sporadic spawning during these months,
especially as in one or two cases the mantles showed little
difference in thickness from those of a spent “ fish ”? (0-7—0-8
mm.). This thinness, however, was due to poor condition; the
mantle consisted of connective tissue, and a few immature eggs
or sperm sacs, and did not show the typical collapsed con-
dition containing but a few residual ripe reproductive elements,
which one associates with a spawned mussel.
The differences in the weight and condition of the samples
for April and May in 1921 show that a short and thorough
spawning had taken place between these two months. The
spring of 1922 exhibits a less well-defined spawning period.
One or two mussels of the March sample ran with spawn when
being handled. Millions of fry had settled on the Morecambe
Skears in mid-April, which (if the estimation that it takes
about a month for the larvae to settle down* is reliable)
suggests spawning in March and possibly in February.
The April sample also showed a condition where some
mussels were full and others not, and it was only after
examination of some shellfish sent in May that one felt sure
the spawning period had come to an end.
Proteid.
The amounts of proteid have been obtained by multiplying
the Kjeldhal nitrogen values by the usually accepted factor
6-25, This assumes molluscan proteid to be the same in
empirical composition as that of the higher animals, and must
therefore be adopted with some reservation. Factors obtained
from the amount of nitrogen in fat-glycogen-ash-free substance
give somewhat higher values, but they vary, and the experi-
ments cannot be regarded as definitive. Whatever factor is
* Johnstone, ibid., p. 38.
209
used will not alter the relative values of the proteid throughout
the year, but is certain to affect the amounts of carbo-hydrates
obtained by difference, and may explain, in part, the higher
percentages of carbohydrates so obtained, and the corresponding
glycogen estimations, in those samples where the latter were
taken. Undoubtedly the percentage of nitrogen in mussel
proteid is not constant.
The amount of proteid rises throughout the season from
the spawning time in early spring, until the eve of the next
spawning. There is a slight depression about February in
both years, which seems to occur, however, in conjunction
with a fall in general body weight. There seems little doubt
that, on the whole, there is an increase up to the time of
spawning.
From May the proteid percentage in the dry-ash-free
substance slowly falls until September and October, and then
rises again to a maximum in the following March. Since the
actual amount of proteid is increasing when the percentage
depression shows itself, this increase is obviously not pro-
portional to the rest of the tissue during September and
October, when there is a rapid formation of carbohydrate
material.
Carbohydrates.
The carbohydrates differ materially from the proteid and
fat as regards their variation throughout the year. There is
a slow but steady rise up to the months of September and
October, a tendency to form a second maximum in December
of both years, and then a rapid decrease until March. The
percentages of carbohydrate in the dry-ash-free substance
shows essentially the same variations, and in the first year
the percentage value rises again up to the spawning in April.
The relative abundance and stability of glycogen in the mussel
have been referred to in the previous paper, and the conclusions
0)
210
have been borne out by subsequent observations. Water
extractions carried out in a Soxhlet apparatus upon mussels
which had performed the railway journey from Morecambe,
and subjected to the Mohr-Bertrand method of volumetric
estimation for glucose, after precipitation of the proteids in the
solution with basic lead acetate, gave no reaction. Yet the
water extraction is fairly effective, as is shown by the fact that
in the sample for April 1922, the solution, after inversion,
gave a glycogen return of 0-862 °% on the wet substance,
whereas a glycogen estimation by Pfliiger’s short method gave a
value of 0-992 °4 which is not much higher. In this connection
it is interesting to compare the results of glycogen estimations
made from the wet flesh, and then from the dried powder of the
same sample: the following results are expressed as_per-
centages on the wet substance, and were obtained by Pfliiger’s
method except where otherwise stated.
The percentage of Glycogen in the wet substance—
Calculated from wet flesh. | Calculated from dry powder.
June 23, 1921 ...... 4095 2°733
INOver li LOZ earns 3°844 0°704 (water extraction)
Dec. 16, 1921 ....... 2-699 ree
(| 1:252 (water extraction)
Extractions from the dry material of these samples were
also carried out by stirrmg with 0-4 °%% hydrochloric acid and
repeated decanting through filter paper. The solution
obtained failed to reduce Bertrand’s solution. This suggests
that the glycogen may be broken down into other material
than glucose.
The question of variation in the quantity of glycogen
seemed of such importance that, in spite of the labour entailed,
estimations were performed for the later samples. Pfliiger’s
method was adopted, and after inversion the glycogen was
estimated as glucose, by the Mohr-Bertrand, or Benedict’s
method. Both of these give results which are strictly com-
211
parable, but the former was found to be the shorter, and easier
of manipulation. The results obtamed are given as percentages
in Tables III and IV, and in all cases but one fall below the
corresponding figures for the carbohydrates calculated by
difference. These differences cannot be due entirely to the
wrong use of a constant (such as the proteid 6-25, or that of
0-927 used for calculating glycogen from glucose) because they
vary in amount.
As seen above, there is no sign of the discrepancy being
due to inversion into glucose, before the samples were tested
for glycogen, and this is borne out by sections, which show
great quantities of glycogen, even when the tissue is not fixed
until it arrives at the laboratory. It may be that there is some
non-nitrogenous, organic matter present which exists in other
forms than glycogen and its inverts. This is at once the most
interesting, but, so far, the least conclusive part of the whole
investigation. One fact which is of importance, however,
emerges from the data, and that is that both the relative
amounts of glycogen and carbohydrates by difference are
at a maximum, on the whole, about October, and then decrease
rapidly to immediately before the spawning time. This
decrease in glycogen before the time of spawning is of additional
interest when one studies its distribution in the tissues of the
animal. MacMunn* was’ unable to discover glycogen in
sections of the digestive gland of several invertebrates, cluding
Mytilus edulis, and the study of sections of one or two mussels,
fixed in absolute alcohol on the mussel beds, as well as that of
many sections made from mussels after having been received at
the laboratory, has led to the same conclusion. In all sections,
whether from mussels fixed directly or after they have been
on a railway journey, it has been possible to detect glycogen by
staining with iodine and Best’s Carmine after several fixatives,
in changing quantities throughout the year, in the connective
* Phil. Trans., 1887, part I, p. 257.
21%
tissue of the body and mantle, in the muscle, and even the
labial palps and gills, yet it has not been possible to get the
same staining reactions in the “liver” itself. This means
that if there is glycogen present in the organ, it is either there in
such a form or in such minute quantities that methods which are
successful for the demonstration of it in other parts of the body
are unable to detect it in the liver.
In this concentration of glycogen in the connective tissue,
as well as in the slowness of inversion in the body, Mytilus
seems, to contrast markedly with the oyster. Mitchell* states
that in the Jatter mollusc, glycogen is found mainly in the Jiver
region. In the Report of the Government Chemist for the
year ended 31st March, 1921, page 24, it is stated that deter-
mination of the glycogen in oysters was “ carried out with
difficulty owimg to its rapid change to other carbohydrate
matter immediately after opening the oyster.”
In the light of this evidence it is interesting to compare
the seasonal variations in carbohydrates of the mussel] described
above, with the quantity of glycogen present in samples of
oysters examined throughout the year by J. A. Milroy.f
Speaking of the percentages of dry glycogen in the moist animal,
Milroy says: ‘‘ As regards seasonal variations there is a
gradual rise in the percentage from the beginning of August
until the middle or end of October. This is succeeded by a fall
which reaches its mimimum about the middle of December.
From that period onwards the percentage rises until it reaches
its maximum some time between the begmning of April and
early in May. The percentage then falls until it reaches its
second minimum early in August.”
According to Bulstrode,t oysters in British waters spawn
* Mitchell, Bull. Bureau of Fisheries, U.S.A.. XXXYV., 1915-16, p. 483.
+ Milroy, “‘ Seasonal variations in the quantity of Glycogen present in
samples of Oysters.” Dept. of Agriculture and Technical Instruction for Ireland
Fisheries Branch Scient. Investigation, 1907, No. IV.
{ Bulstrode, 24th Annual Report of Local Govt. Board, 1894-95. Supple-
ment, ““ On Oyster Culture in relation to Disease,” p. 8.
213
between May and August, so that from Milroy’s results, the
percentage of glycogen rises from December to within a month
or two of spawning. Mitchell* obtaimed glycogen in American
oysters in quantities which he states to be similar to those of
Milroy, and he also gives the spawning time as July and
August. The rise in glycogen in late summer is similar in the
oyster and mussel, but from December the variations in the
two animals do not show agreement. For several months before
the oyster spawns, the glycogen content of the animal is steadily
rismg and, although a decrease sets in before the spawning
takes place, the minimum is not reached until this season is over.
With Mytilus there is a rapid fall of glycogen from December
to March, and then a tendency on the whole to a rise until the
time of spawning in April. It is of the greatest interest to
examine the sections stained for glycogen during this period.
In September, although the mantle may be comparatively
thick (2-4 mm.), there is no sign of reproductive products in
the connective tissue; mantle thickness is not necessarily an
index of increasing sexual maturity. The glycogen is seen as
solid lumps lying in the connective tissue cells. From October
onwards, the egg and sperm sacs ramify through the tissue,
increasing apparently at its expense, and grow until they almost
impinge one upon the other. The glycogen, along with fat
globules, is seen to be wedged into the surrounding tissue.
Apparently one reason why there is less glycogen now is because
the sperms and eggs take up the space occupied by the former.
It is to be expected that such rapidly-growing tissue requires
nutriment, and there is little doubt that they obtain the latter
at the expense of the fat and glycogen; but whereas the
former becomes incorporated into the reproductive products,
so far as micro-chemical methods are to be relied upon, there is
no conclusive evidence that this is the case with the glycogen,
as such ; it is apparently converted into some other substance.
* Mitchell, loc. cit., p. 481,
214
The eggs are quite as large a month or two before spawning
as when they are extruded, and during this time when they are
maturing it may be that nutrition is no longer necessary, and
would explain the rise in glycogen just before the spawning
period. This, along with the apparent absence or slowness
of a diastatic enzyme suggests that the glycogen stored up
by the sea mussel is made direct use of in the extraordinary
reproductive activity of this animal.
Fat.
The amount of fat, as we have already seen, is small, and
shows a steady increase up to the time of spawning. The
accumulation of fats throughout the year is well shown both in
frozen sections stained with Sudan III, and in tissue fixed in
Fleming without acetic acid. Sections in October show fat
only in certain liver tubules, and intestinal epithelium. This
increases In amount, and by November the fat is beginning to
show in the growing reproductive products in the body and
mantle. From December onwards there is an accumulation of
fat about the sperm sacs of the males, and in the eggs of the
females, and this condition obtains until the spawn is extruded,
after which time the fat again seems restricted mainly to the
liver.
Enterochlorophyll.
The greenish yellow pigment extracted from the digestive
gland of several molluscs by MacMunn*, and named by him
Enterochlorophyll, is very evident in frozen sections, and
also attracted attention during the extraction of fats in the
Soxhlet apparatus, by giving to the carbon tetrachloride a deep
green or brown colour, until the apparatus had siphoned over
several times. It was noticed too that after a Pfliiger glycogen
estimation the pigment showed itself in the filtered liquid,
and had therefore apparently resisted digesting on the water
* MacMunn, loc. cit., p. 235,
215
bath with 60 % caustic potash. The frozen sections show that
the colour and intensity differ from month to month, although
the years do not repeat entirely the same conditions. The
liver is a lighter green about September, and it is certain that a
dark brown colour, much more intense than at other periods of
the year, appears in March and April, the months which cover
the reproductive period.
MacMunn concluded that the colour was secondary in
nature and derived from the diatoms taken in food. List* and
Dastre and Florescot have shown that the liver can be colour-
fed. This organ of Mytilus certainly shows most colour
during the period of the plankton maximum and when the
spores of algae are abundant. It is interesting to note that
the amount of ash steadily increases up to the two months in
question; since the amount of ingested sand and mud must
affect considerably the ash estimation, this also suggests
a vigorous feeding in the early spring. There is evidence that
the time of most active feeding is from January to April.t
Composition of the Mussel Shell.
Estimations for calcium carbonate and iron were carried
out on shells ground to a powder in a mortar, from various
samples. The water percentage was estimated from the
difference in the weights of a sample of powder before and
after drying to constant weight in an electric oven at 100°C.; this
was carried out immediately after the grinding down of the
shells. To obtain the amount of calcium carbonate present,
a sample of approximately 0-5 grammes of shell powder was
taken, and dissolved in dilute hydrochloric acid, after the organic
matter had been removed by ignition in a crucible. The
solution was made alkaline with ammonia, and then acetic acid
* List, “Die Mytiliden,” Fauna und Flora des Golfes von Neapel,
XXVII, 1902.
+ Dastre and Floresco, C. R. Ac. Sc. Paris, T. 128.
t Herdman and Scott, loc, cit., p. 41.
216
added until there was a slight excess. After heating, a boiling
solution of ammonia oxalate was added, and the precipitated
calcium oxalate allowed to stand overnight. It was then
washed carefully with boiling water to remove any excess of
ammon. oxalate and received on to a filter paper. The paper
was pierced and the precipitate washed into a measuring
flask with boilmg water and warm dilute hydrochloric acid ;
sulphuric acid was then added to dissolve the precipitate
completely, and to get the oxalic acid into solution. After
making up to 250 cc., the solution was titrated against »/10
potassium permanganate, and from this titration the amount of
CaCo; found.
From several estimations which were made in duplicate
it would seem that the method of sampling was not to be
trusted. The chitinous covering of the shell, and also its
organic matrix, probably did not allow of a homogeneous mixing.
It has been thought as well to give the results in Table V, with
the results of a second estimation, when these were taken, in
brackets.
The same error of sampling would of course apply to the
iron estimations. Here 0-5 grammes of the powder was
ignited, dissolved in HCl, and then the iron present was
converted into the ferric state by careful addition of potassium
permanganate to the solution.
The estimation was carried out colorimetrically with the
aid of potassium thiocyanate, against a standard solution of
ferric iron.*
* See Sutton, Volumetric Analysis.
217
TABLE I,
AVERAGE WEIGHT OF| AVERAGE WEIGHT OF || AVERAGE WEIGHT OF
SHELL AND FLESH. SHELL. Wet FLESH.
Date. - -
Rest of Rest of Rest of
6 mussels. | sample. | 6 mussels.) sample. | 6 mussels. | sample.
1920
May 21 13:1 130 6:9 6:9 671 61
June 10 15°8 16°4 10-0 lf) wis 58 56
July 7 | 12-0 12°5 62 | 74 59 ol
July 26) 158 14:2 9°9 | ae 5:9 ake
Aug. 20] 18:3 18°3 10°8 | 10-4 45 78
Sept.13 | 18-0 17°4 10-4 9°6 76 ‘7:8
Oct. 8| 17:0 15:0 79 69’ 9°1 81
Oct. 29 17°6 18°9 9°4 9°6 8:2 9°3
Nov. 25 16:0 7/58 8-0 8-2 8-0 9°]
Dec. 17 20°8 20°4 8-4 8:6 1223 11°8
1921—
Jan. 13 19:7 7/27 9°2 79 10°6 9°8
Feb. 5 19-0 20°6 8:3 9:2 10°7 11°4
Mar. 2 18°7 15°8 9°5 8:2 9:2 76
Mar. 24 | 22:4 20°5 Hite 10°6 is? 9°9
April 22 18°9 18°6 9°5 9°6 9°5 9-0
May 20 14:8 last 8:7 8:7 61 6:9
June 23 19°8 19°5 11:2 Tiles} 8°6 8:2
July — 906 50 ee aoe Bb ae
Aug. 16 14:4 16°5 871 9°6 6:3 70
Sept. 15 21°4 17°1 10°9 8:9 10°4 8:2
Oct. 18 14:7 14:3 6:2 6:4 8:4 79
Nov. 17 ps3 16:1 6:3 15) 9-0 10°6
Dec. 16 Wea 18°5 7EU 79 10:0 10°6
1922—
devil, ie 19:9 159 10-2 81 9:7 isd
Feb. 17 17:0 15s les | 6:5 9°6 86
Mar. 15 20°0 23°9 10-0 | _aliles: 10-0 12°6
April 20 14°3 1st 6:8 6:2 105; 6°9
19
April 22
218
TABLE II,
Weights of six mussels from each sample.
21—
Jan. 13
Feb. 5
Mar. 2
Mar. 24
May 20
June 23
July —
Aug. 16
Sept. 15
Oct. 18
Nov. 17
Dec. 16
22——
Jan. 17
Feb. 17
Mar. 15 |
April 20
May 13
Weight of
94°
109°7
107°9
101°6
105°7
96°0
124°6
118-4
1140
112°2
134°5
113°6
88°6
118°7
86°4
128°1
88-0
DIES
106°5
119-4
101°7
120-0
85°8
82°9
| Weight of
shell and flesh. |
|
shell.
OAS
BR onl rHOUOpE
IA: SO] CHNWMES
ope rE
Weight of
wet flesh.
“1 OTP BW OO we
Bea SSH OU CUCUCUHS OS
KOR Oke LD +10
Weight of
dried flesh.
i
COOP S SAAMI
ORWO WOR Te bo
—_
——
: AS [he Uae NS)
NNO’ Or He Ww Oh ©
a
SSH: oar
Weight of
water.
OS Soe
PPP RO Bw] Roo
20) ire : ;
moomnon* ow wwodn
ww SSS:
219
TABLE III.
Percentage composition of the wet substance.
| | Ones || Carbo- |
Date. Water. Dried Proteid (Carb. Ash. hydrate | Glycogen
| flesh. (N 6:25). | tetrach. | (by (Pfliiger).
extract). difference). |
1920— |
May 21 85:9 141 8:2 0°6 09 | 4-4
June 10 85-4 14°6 | 8:5 0-5 1:2 44
July 7) 83:9 Lo 5) 86 (Ey | BR 4:5
July 26 80°1 19°9 10°8 1-2 | 15 6°4
Aug. 20 | 78:0 22:0 118 15 16 7
Sept.13 | 76°5 23°5 12°5 15 7 | 78
Oct. 8 | 80°1 19°9 9:7 1:3 a 68
Oct. 29 | 79:0 21-0 11:0 14 one 6:7
Nov. 25 | 80:3 19+7 10°8 16 1:9 5°4
Dec. 17 82°4 17°6 SPI 11 1:8 56
1921—
Jan. 13 811 18°9 We 15 0:2 5°5
Feb. 5 82°6 17-4 10:7 13 18 3°6
Mar. 2 81:8 18-2 Leys 15 2°4 2°6
Mar. 24 83°3 16°7 10°9 16 271 271
April 22 80:0 20:0 12:0 21 2°4 3°5
May 20 | 85-4 14-6 86 0-7 2:2 371 ae
June 23 83:0 17:0 86 1121 2°7 4°6 4°1
July — 50 ane Se sae oe 308 bot
Aug. 16 80°1 19:9 10°6 16 19 58 ce
Sept. 15 80-1 19°9 9°8 13 LST 1 2°5
Oct. 18 80°3 19:7 10-1 1-0 2°5 61 6°6
Nov. 17 81:2 18°8 9:7 1-2 2°4 55 3°8
Dec. 16 | 81°4 18-6 10:2 1°5 1°9 50 dl
1922—
Jan. 17 84:2 15°8 9°6 10 18 a4 113
Feb. 17 84°6 15-4 9°6 1:2 2°2 2-4 05
Mar. 15 81-1 18°9 119 1-2 3°5 2°3 0-2
April 20 83°2 16°8 9°8 1:3 3'8 1-9 1-0
220
TABLE IV.
Percentage composition of the dry, ash-free substance.
Date. | Proteid. Oil. Carbohydrates Glycogen
(6 x 25) (Carb. tetrach. | (by difference). (Pfliiger).
extract).
1920—
WEN PRL Saccce 62°3 47 33°0 |
June 10 ...... 64:1 3°9 32°0 |
AEN? 2) sane 62°4 | 5°2 32°4
July 26 ...... 58°7 68 34°5
Ang, 20h) | ors ip 35:0
Sept. 13 ...... | 57°3 69 35'8
Oct) 8 cace0. 54°6 7:0 38-4
Ole PAD sconce 57:7 | 75 34'8
INOWs) 25) seca 60°5 9°3 30°2
Dectaliieeccss 57°6 | 7:2 35:2
1921—
Jans) 1Si tees: 62°3 78 29:9
INS occa 68°7 81 23:2
Mars 2) sss. 74:1 9:7 16:2
Mar. 24 ...... | 74:2 10°7 151
April 22 ...... 68°1 12:1 19°8
Maiyie20 ee. 69°3 54 25:3
June 28 ...... 59°7 74 32°9 28°5
July — ...... 568 3 50C eee
USS Giwoce est 58°7 9:0 32°3 alte
Septilote.cs 54:0 6:9 39°1 13°8
Oct wI8¥-52-2- 58°5 6:0 35°5 38°6
INOWe Uae ccs: 58°7 75 33°8 23°4
Decy Gees. 61:2 9:0 29°8 1671
22
rig INE Geaene 68°8 74 23°8 9-2
1Slsy LZ couse 73°0 89 18:1 4:3
Mary 15) cess. 77:0 76 15°4 1:4
April 20 ...... 75°7 10:2 14:1 76
221
TABLE V.
Percentage composition of the shell.
1920—
Oct. 29
Nov. 25
Dec. 17
1921—
Jan. 13
Feb. 5
Mar. 2
Mar. 24
April 22
May 20
June 23
Aug. 16
Sept. 15
Oct. 18
Nov. 17
Dec. 16
1922—
Jan. 17
Feb. 17
Mar. 15
April 20
UNDRIED SHELL.
DRIED SHELL.
Water.
1:07
ee
Oo
“11
HOH WSSoSoooo
wor 710 0O+1
KEOCORRWHaIRWOR
So -1to
Sass,
o bd 0
oo 19
95°31
95°35 (98°39)
| 95:31 (96:69)
| 94:90
95°31
| 95°74
96°90
| 98-06 (95°43)
95°79
99°38
98-05 (96°29)
98°22
97°31
| 99:26
| 98-25
| 97°27
Fe.
0-08 (0:06) |
0:07 (0-07)
0-08
0-04
0-02
0-05
0:04 (0:05)
0-007
0-002
0-007
0-007
0-01
0-02
0-008
0-007
0-003
Organic matter, ete.
BY 222,
DISEASES AND PARASITES OF FISHES.
By JAS. JOHNSTONE, D.Sc.
CONTENTS. PAGE
Septic Ulcers in Cod; Malnutrition of North Sea Fishesin 1921 ... 222
Various Fish Tumours—
(1) A Benign Tumour ina Plaice ... aes wa ik fea, PAT
(2) Sarcoma in a Haddock ... Se aes ast nis ao) lh
Cestode Degeneration Cysts in a Trout ... iss ae ace .. 230
The ‘‘ Oyster Parasite,’ Gasterostomum gracilescens... ar seg | BI)
A Myxosporidian in a Hake 406 50¢ Sa abe oe ZOD
Septic ULcers In Cop AND OTHER MARINE FiIsuH:
MALNUTRITION OF NortH SEA FISHES IN 1921.
Between September, 1921, and March, 1922, a number of
specimens of diseased cod and other marine fishes were received :
all of them were taken in the 8.W. part of the North Sea.
The sendings were: 27th Sept., 1921, codling; 24th Oct.,
cod; 27th Oct., cod; 4th Nov., cod; 7th Nov., cod, 2 plaice ;
17th Nov., 2 plaice, codling, haddock; 24th Nov., cod;
28th Nov., plaice, sole ; 20th Jan., 1922, cod; 14th Jan., cod.
All these fish were taken inshore, or at a greatest distance from
the land of about 60 miles.
The same general affection was displayed by all these
fishes. There were large, shallow ulcers on the surface of the
body, destroying the skin and eating down into the flesh to a
depth of about one quarter of an inch. In most cases there
were several ulcers, or sores, and usually on both sides of the
fish. In several cases there was healing—this I refer to later
on. Sometimes there were red, highly-inflamed patches on
the skin, without erosion of the latter. In other cases there
were places where there was no ulceration, but where the scales
were apparently raised up and swollen, and with swellings in
the skin below the scales.
Usually the fish were in “poor” condition, or were
223
> and in several cases there was extreme emaciation.
* slinks,’
This was especially characteristic of one of the plaice—where,
however, there was healing of the ulcerated sores. In some
of the cod the emaciation, particularly on the head and
shoulders, was very great. In two cod there were other
malformations, a shortening of the length of the fish relative
to its girth. This was due to a twisting of the backbone, the
latter having a slightly spiral shape.
The general appearance of the ulcers is, of course, highly
variable. Sometimes they are little more than inflamed spots
on the skin, but as a rule there is complete destruction of the
latter over a greater or less area. When this occurs there is
a typical “sore,” the boundary of the ulcer bemg rather
sharply marked and its floor being formed by the underlying
body muscles, the skin being completely destroyed. Thus
there is a shallow cavity of irregular shape, partially filled with
pus and products of necrosis, including much blood. The
ulcer is never very deep, though occasionally there are small
pits going down into the muscles. Generally the edges are
highly inflamed, and the inflammation often extends over the
whole floor of the shallow cavity, though sometimes the colour
of the latter may be yellow-white. Beneath and round the
eroded area there is always a margin of inflamed skin or
muscular tissue.
In the plaice examples all stages of healing were observed.
One fish was very greatly emaciated, the skin, in some places,
‘‘ clinging to the bones.” There was an ulcer of about 3 inches
in diameter on the coloured side, but the greater part of this
had healed over and there had been regeneration of tissue.
Near the centre were the remains of the ulcer, as a cavity
about an inch in diameter, at the bottom of which several
vertebre, with their hemal species, only very lightly covered
with colourless connective tissue. The whole area was thus
skinned over, and the greater part of this new skin was
22.4
pigmented quite normally. In another plaice the process had
gone still further and, though the ulcerated cavity had not
completely filled up, the edges had smoothed down and the
pigmentation had, except for two small white spots, been
completely restored. This was on the coloured side of the fish :
on the colourless side was a patch of skin about an inch and a
half in diameter where there had been an ulcer. This was
level with the rest of the skin and of the same colour. In all
these cases of healing it is notable that there was no regeneration
of the scales. It would appear that, once destroyed in a fish,
these structures are not formed again.
Often the first indications of the lesion are the apparent
swellings of the scales. Underneath a small patch of the latter
there is an obvious thickening, and the margins of the scales
become loosened so that their outlines are the more easily
seen. Each scale lies in a sort of dermal pocket and is covered
over with epidermis, and all these structures share in the
general disintegration of tissue which is the result of the
inflammatory process.
On the whole, then, the sores are very obvious, very
familiar, in a kind of way, and are so repulsive that they are,
of course, sufficient to ensure the instant rejection of the fish
as an article of food.
Sections were made of various parts of the ulcers, including
the edge, and other lesions where the surface was unbroken,
but where there was a region of inflammation beneath the
skin. Smears from the pus on the open sore were made and
stained, and these showed numerous bacteria, which had, of
course, infected the sore after the latter had been formed.
Staining of the sections so as to demonstrate the presence of
bacteria had very variable results: in some cases the latter
could not be detected. -What was seen were only abundant
leucocytes, blood corpuscles, and broken-down tissue in
general. Round the margin of the ulcer there is a kind of ring
225
of connective tissue crowded with small, round leucocytes and
containing an abundant blood supply. That is all that can
sometimes be found. In other sections, however, even when
the surface of the skin is not eroded, but where there is only
inflammation, the presence of micro-organisms can be seen.
There are apparent spaces in the sub-dermal or dermal tissues
filled with small bacilli, very evident when the section has been
stained only with carbol fuchsin. Except for these, and a richer
blood supply than ordinary, there may be no evidence of a
pathogenic condition. In other cases there are plenty of
bacilli lymg among the leucocytes in the marginal parts of the
sores, even although none may be found in the pus in the
central parts. Evidently, then, we have to deal with infections
—the ulcers may be regarded as generally septic ones in spite
of the condition that, in some cases, the micro-organisms are
difficult to detect. There was no opportunity for making
cultures, or for studying the living fish. This kind of investi-
gation demands an amount of time and special training which
we are, as yet, unable to give to the work. The only special
tests that were made were those for acid-fast bacilli, and in no
case were such successful.
The interest of these specimens of ulcerated cod and other
fishes was increased because of various circumstances. The
number of diseased fish occurring in the North Sea arrested
attention during the last winter. Thus: “ The skippers report
that they have never known such a year as the present one for
poorness in the quality of fish and the number of fish seen with
sores. They report that the sea is extremely dirty at all
places. It may be of interest to you to know that the herrings
landed this season at Yarmouth are all of very poor quality,
having the appearance of being starved.” Again, ‘‘ The general
condition of the cod caught in the deep water has been extremely
poor. The majority of the fish are poorly furnished and are
termed ‘ slinks ”.”
2
226
The North Sea herrings were also abnormal in quality in
1921. Thus a packer of tinned herrings of high grade says:
“This year’s pack has something the matter with it. The
flesh of the fish is grey to brown instead of light, like a chicken.
The liquor in the tin is watery and dark and bitter instead of
light, thickish, and pleasing to smell and taste.” These defects,
it must be understood, were comparative ones, for even this
1921 pack of herrmgs were, to the ordinary person, of very
high quality. Nevertheless, to the trained eye and palate the
result of the packing operations was inferior to that of 1920.
Why ?
What one heard about was, on many sides, the “ still and
dirty ’’ water (which meant unusually large quantities of plank-
ton organisms). The abundance of oil was also blamed, and
‘
the mines and dumped explosives which were “ exuding their
filthy, deleterious chemical compounds to the detriment of the
plant life upon which the little animals forming the herring’s
food, feed.”
It is, of course, quite impossible to say, with the information
that we have, whether the general poverty of nutrition charac-
terising many fish, at certain times of the year, was due to any
one, or several of the suggested causes. The ulcerated cod
which are described here may have been such because of some
form of poisoning due to the presence of products of decom-
position of explosives. Not all these sores were septic, and
in some there was little indication of organisms in the pus.
It is possible to produce a septic pus by the local action of
various chemicals, such as mercury and copper and their salts,
and so some of the ulcerated fish may have become so by such
means, Still other sores were certainly septic, so that, on the
whole, it is not possible to state definitely what were the causes
of the lesions.
07
Various Fiso Tumours.
(1) A Benign Tumour in the Plaice.
A plaice of 164 inches long, a female in very fair condition,
was sent to us by Mr. King, the Collector of Statistics at
Yarmouth. The fish has a very typical tumour on the dorsal
fin, on the coloured side. The growth is about 33 cms. in
diameter, and is raised up from the general surface of the fin
about 3 cms. It is nearly spherical, except that it is a little
flattened in the same plane as that of the fish. It is pigmented
very much in the same way as the fin and there are several
very noticeable blood vessels running just beneath its surface.
It is firm, but elastic. It has all the appearance of a human
“wen,” such as one sees sometimes on a man’s neck, except
that the fish tumour has a rather narrow attachment to the
part on which it is situated.
Sections show the structure to be that of a typical fibroma.
At the periphery there is no proper skin, resembling that of
the fish: whatever cuticle there is is rather transparent.
Beneath the surface there is a layer of strong elastic tissue
and on the surface itself this merely becomes rather more
compact than it is in the deeper layers. There is a very definite
“capsule? made up of this dense elastic tissue, and below
this, and occupying the central part of the tumour, there is a
loose connective tissue, the fibres of which are wavy, but run,
on the whole, in lamine concentric with the surface. Here
and there are a few small blood vessels and capillaries, and
sometimes a few rounded, connective tissue cells, but otherwise
the histology presents no remarkable features.
(2) Sarcoma in a Haddock.
The specimen described here was sent to me by Mr. F.
Stokes, Port Sanitary Inspector at Grimsby. It was a haddock
of large size caught by a Grimsby codman and landed at that
port. It is of some interest because very much the same
228
kind of affection has been seen in several cod, and it is important
to ascertain whether or not such conditions are of exceptional
occurrence.
The fish was much emaciated, so that, as might be expected,
the presence of a large, malignant tumour has a considerable
influence on the conditions of health. In such cases as this
we may expect some diffusion, through the body, of the products
of the growth. This, I take it, is the justification for the
condemnation, as articles of human food, of fish suffermg from
bd
malignant, “‘ cancerous ”’ growths.
The growth in question is situated on the top of the head,
above and behind the eyes. It is represented, about half
natural size, in Fig. 1. There are two principal tumours, or
Fig. 1.
centres of growth, and these have run together. Cutting down
into them we find a general softening, or necrosis, and this
has gone so far as to lead to a breaking through the surface
at the top of the foremost growth. There is a peripheral zone
of firm tissue, but internal to this the tumour is semi-liquid
in consistency.
The histology is represented, under a magnification of about
10 diameters, in Fig. 2. The figure represents a section taken
Malignant 7/ssue
Degenerating, S
A
‘
eee
,
Fie. 2.
at the margin of the tumour, that is, at the growing part.
The skin is shown diagrammatically, with several scales in
position, each in its epithelial pocket. Below these is the
dermis, here a rather thick, fibrous layer. To the right of the
part represented in the figure this dermal layer thins out and the
scales disappear, though the ordinary pigmentation of the skin
230
remains. At the central part of the tumour the integument,
so altered, becomes very thin and finally breaks through at the
region where the internal part of the tumour is undergoing
necrosis.
Cutting down into the latter, along its middle line, we
find this general liquefaction, and the necrosed contents rest
directly on the bones of the skull. In the firmer parts we have
the fibroid type of structure—fine fibres running in various
directions and, here and there, a few round cells. The latter,
however, do not characterise the histology, which is of the
nature of that seen in fibromata rather than in sarcomatous
growths. The malignancy is evident, however, when one looks
at the growing margin. On the left-hand side in Fig. 2 are a
number of isolated muscle fibres, here cut obliquely: in a
section of this region in a normal fish there would be a thick
layer of muscle bundles running in various directions. Here,
however, these are degenerate and are represented only by
detached fibres, becoming fewer as the tumour is approached.
The malignant tissue is represented by fine stippling in the
figure, and this is seen infiltrating the muscle tissue, intruding
between the fibres. It is, as in all other fish sarcomata that
I have seen, this intermuscular connective tissue that takes
on the conditions of malignancy and gives rise to the sarcoma-
tous tumours.
CESTODE DEGENERATION Cysts IN TROUT.
The viscera of a 10-lb. yellow trout were sent to me by
Mr. J. Ritchie, of the Perth Natural History Museum. These
structures contain a number of cysts which are so very remark-
able that a description may be interesting even although the
parasites responsible cannot now be identified.
The peritoneum over the liver and pyloric ceca bear a
number of little oat-shaped bodies which look almost like seeds.
They are about 4 or 5 by 8 to 10 mm, in their lesser and greater
231
diameters. They have a kind of papery lustre and are hard.
Some of them appear to be embedded in the liver, but they
can generally be separated, when it is seen that they are
attached to the peritoneum by slender pedicels.
They are easily cut. Fig. 3 represents a transverse section
through one of them. At first sight the appearance is very
Fie 3.
puzzling, but on dissecting a cyst one finds that a firm nucleus
can easily be “ shelled out.” Then the nucleus can easily be
dissociated into two or four collapsed thin-walled cysts that
were evidently spherical when they were in their original con-
dition. So Fig. 3 shows four of these cysts, crumpled together
232
by mutual pressure and fitting into each other, so to speak,
in the way shown in the section.
The outer wall of the whole cyst is fibrous in structure
with a thin, external serous layer, and among the fibrous layers
there are a few blood vessels. This part, therefore, belongs to
the host. The fibrous layers send inwards a few trabecule
between the secondary cysts, but apart from this there are no
other tissues. The internal, secondary cysts have walls of quite
a different nature, these consisting of an apparently homo-
geneous substance (it is represented by the thick black bands
in Fig. 3. It may be called “ elastic tissue,” though it is not
exactly like this. It is yellow in colour. Within these
secondary cysts there is nothing but an unrecognisable cell
debris containing much oil, which tends to coalesce in droplets
when the cyst is opened and scraped out. No remains that
can be ascribed to known parasites can be identified—no hooks,
spines, or calcareous corpuscles. This is rather a difficulty in
assuming that we have to deal with a degenerate cestode larvee,
for the hooks and spines are very persistent. Still, the parasite
may not have had any skeletal structures and the calcareous
corpuscles may have been dissolved for the specimen had been
kept for nearly two years in spirit and part of it was fixed in an
acid preservative.
A taxidermist who had the fish supposed that the cysts
were ova that had been eaten by the fish, but this is obviously
not the case. Nor are they ova that have not been extruded
for there is no trace of egg structure. It is exceedingly likely
that they are really small groups of Plerocercoid larvee which
have degenerated. In many fishes there are collateral life-
histories for the contained Cestode and Trematode parasites :
that is, there is an infection arising by the fish eating some
animal which contains the larve of the Cestode. Now the
latter has usually “ definitive’ hosts, one which contains the
larvee and which is eaten by the definitive final host, where the
2338
Cestode comes to sexual maturity. If, however, other fishes
than the definitive final host become infected the life-history
of the Cestode cannot be completed, and the larve develop
no further than the Plerocercoid stage, which finally dies and
degenerates. But in so doing there is some reaction on the part
of the collateral host. That is, there is often some kind of
covering laid down by the tissues of the host and this may
take extraordinary forms, as for instance, when typical pearl-
like bodies are formed round the unrecognisable remains of a
parasite of some kind. This is what has, no doubt, happened
in the specimens we have. Plerocercoid larve of tetrarhynchid
tapeworms are very common in many teleost fishes, where they
appear as little cyst-like bodies attached to the peritoneum. In
teleosts the development of a Plerocercoid larva ends the life-
history of the Tetrarhynchus, which then dies and degenerates ;
but in rays and dogfishes the larva completes its metamorphosis,
gets into the intestine and becomes a sexually mature Cestode.
Here, then, we doubtless have some Cestode (but evidently
not a Tetrarhynchus) which has so entered a cul-de-sac in its
life-history, has died, become invested in a cyst wall which
shields the host from its further reaction, and so gives rise to
these peculiar bodies.
Tue “ Oyster Parasite,” Gasterostomum gracilescens.
This is the well-known Bucephalus haimeanus, Lacaze-
Duthiers.* We have found it already in this district, but
never in such a heavy infection as in this case. It occurred in
cockles that were being dissected in a vacation Biology course,
held at the Piel Laboratory in August, 1921. The infected
molluscs were bright yellow in the upper part of the visceral
mass, and out of 55 specimens examined 3 were infected. The
* See Miss Lebour, ‘A Review of the British Marine Cercarie,”’
Parasitology, Vol, IV, No. 4, 1912, p. 424.
234
235
parasites occur in long, greatly-tangled, tubular and branching
sporocysts. These are represented in A and F, Fig. 4. They
are full of larvee in various stages of development, but these
are rather more numerous than are shown in the figures. The
fully-developed Cercariz are represented in Fig. 4, B and C,
and less mature ones are shown by D and KE. The body of the
worm is covered by very closely set spines, arranged in trans-
verse rows. The tails are extremely long and highly mobile,
retaining this mobility for some time even after they have
been accidentally detached from the body. The living sporo-
cysts and larvee make most interesting objects, but apart from
their occurrence there is nothing remarkable to record about
them. Except for the very long tails their characters are just
such as have been described by Miss Lebour.
A MyxXoOSPORIDIAN FROM THE HAKE.
In February of this year, Dr. Hanna, Port Medical Officer
for Liverpool, sent me the head of a large hake which exhibited
several tumours. There were three of the latter: one situated
just in front of each orbit and the third exactly between the
other two and on the roof of the skull. Each was about an
inch in diameter and was raised above the general surface by
about half to three-quarter inch. As usual the skin was much
broken over these tumours. Cutting down into them it was
found that they were cartilaginous and that each was full of
little opaque specks, about one-half a millimetre in average
diameter. This, of course, at once suggested the nature of
the tumours—hypertrophy of the cartilage of the head due to
an extensive infection by a Myxosporidian parasite. In the
Twelfth Annual Report of this Laboratory (for 1903, pp. 46-62),
Dr. H. M. Woodcock described various Myxosporidian parasites
from local fishes, including one from the cartilage of the auditory
236
Capsule of a plaice: this he called Spherospora platesse. In
a later report (No. 15, for 1906, pp. 207-208) Dr. Woodcock
describes another Myxosporidian which occurred in the sclerotic
of the Norway Pout, Gadus esmarkii, and this he called
Myzxobolus esmarkii. Since then we have found that similar
Myxosporidia are not at all uncommon in the cartilage of the
auditory capsule of whiting and cod, and these parasites are
probably identical with the latter one characterised by Dr.
Woodcock.
In the hake described here the sclerotic of one eye is
heavily infected with the Myxosporidian cysts in a way that is
quite similar to that seen in the specimen of Gadus esmarkii
referred to above. Not only so, but almost everywhere in the
skull; wherever there is cartilage the same condition exists.
There are blunted projections into the mouth, and on cutting
into these they are seen to be cartilaginous and to contain
numerous Myxosporidian cysts. Evidently we have to deal
with a very heavy infection.
Rough sections were made of the tumours on the head
and these were found to consist of a fibrous cartilage. Round
each cyst there appeared to be a thin limiting membrane, but
there was no fibrous capsule. However, the fixation had been
a simple, weak formalin one, and so the preservation was too
imperfect to admit of close study of the histology.
Fig. 5 shows two of the spores. A is stained with Mann’s
methyl-blue-eosin and B with carbol fuchsin. The spores are
lenticular in shape, but very nearly spherical (10 by 9 ~) when
seen on the flat. There are two oval polar capsules, each
measuring about 4 w in longest diameter. There is a large
iodinophilous vacuole. The fixation was so imperfect that
none of the stains (Mallory and also hemalum were used)
were able to demonstrate the nuclei. No polar filaments
could be seen.
237
So it is perhaps risky to attempt to identify the organism,
but it may be safe to place it in the genus Myzobolus; and it
resembles the form called M. esmarki, by Woodcock, so closely
that it is not improbable that such is its species.
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LANCASHIRE AND WESTERN
Se wblisktiikhis, JOINT COMMITTEE.
el Oe)
ON THE
MUEISoE ES
IN THE RIBBLE ESTUARY.
Report on the Mussels from the Ribble
Training Wall.
By W. Birtwistle.
A preliminary topographical survey of these mussel beds
was made in July 1921 by Mr. Scott, and a provisional report
was then made tothe Committeet. The location of the mussel
beds, the positions of the sewer outfalls up to date, and the
characters of the sewage effluents were observed. Further,
the directions in which these effluents moved were carefully
noted, as well as the general appearance of the mussels and
their surroundings. It was then decided that a bacteriological
examination should be made of those mussels which, from
topographical evidence, would be expected to show the
greatest and least possible pollution respectively.
The locality chosen as probably showing the greatest
pollution was the Church Scar Bed, and that showing as little
as any was at a point on the North Training Wall, 13} miles
from the dock gates at Preston. The exact position is opposite
the No. 2 Gas Buoy shown on the chart of the 1920 survey of
the Ribble and Estuary.
DESCRIPTION OF THE RESPECTIVE LOCALITIES.
Church Scar Bed.
This bed extends from about 500 yards west of Lytham
Pier, adjacent to the northern bank of the Channel for about
1,000 yards, ending about the tenth mile. Occupying a some-
what irregular shape, its greatest breadth from the Channel
boundary is about 150 yards, opposite St. Cuthbert’s Church,
from which it takes its name. It bares at low water, when
+ Printed in Superintendent’s Report for Quarter ending 30th Sept., 1921.
the mussels are gathered by hand. The mussels are matted
together and form wave-like undulations on a soft, slimy
mud—in some places 18 inches deep. When the bed was
visited in the hot weather of the summer, it had a most
offensive smell, not unlike that of a cesspit. This was not
noticed on this second visit in November, and the bed was
much cleaner, probably as a result of abnormally high spring
tides and much rainy weather. These physical conditions will
probably tend to minimise the pollution of the mussels. The
sreatest contribution to the pollution may be expected from
the Lytham and Ansdell outfalls, which are situated about a
mile and a quarter to the N.W. from the centre of the bed.
There are two outfalls about ten yards apart, and these convey
practically all the sewage of Ansdell and Lytham. The
effluent is quite untreated, and contained much paper and
feeces. The direction of flow at low water is m a south-
easterly direction towards Church Scar bed. About 300
vards away, however, it tended to flow south, and was lost
in the innumerable channels on the sand bank. Thus, the
effluent does not actually flow over the bed. The ebb stream
itself, however, ebbs mainly in the direction of and over the
westerly end of the mussel bed, so that it is reasonable to
suppose that towards the end of the ebb the bed is extremely
liable to pollution. Another probable source of temporary
pollution, although perhaps not great, is a large barge which
is permanently moored over the bed, and which grounds at
low water. This barge is fitted to accommodate gangs of
workmen for varying periods, so that here is a pollution
actually on the bed. .
Training Wall. Gas Buoy No. 2. 153 miles from Preston
Docks.
This point is on the Northern Wall, about two or three
feet above the level of dead low water at ordinary spring
tides. The impression one gets here is that the mussels are
clean and well scoured. There is neither smell nor mud, and
they are evenly distributed on the shingle and stones forming
the top of the wall. The main sources of pollution of these
mussels would be the effluent from the Preston Sewage Farm
at Freckleton, between the third and fifth miles on the
northern side of the Channel. The only treatment this
sewage gets is coarse screening, sedimentation and irrigation
on the Sewage Farm; it is simply sewage with the coarser
matter removed. This effluent is run off into the Channel,
and has to flow about nine miles before reaching the mussels
under consideration, and it is probable that the dilution must
largely reduce the risk of serious pollution. Another probable
source of pollution was evident in the effluent from the Lytham
East sewer. This drains down a mud gutter, and empties
into the channel about 70 yards in front of the Pier at dead
low water. This is about the ninth mile, or four-and-a-half
miles away from the mussels under consideration. The
volume of effiuent is small, and it has four-and-a-half miles
to travel down channel before it reaches the mussels; the
risk of pollution is not serious. A very important source of
pollution is the effluent from the Ansdell and Lytham outfalls
referred to as probably polluting Church Sear Bed. This
finds its way into the Channel, and must be included as one
of the sources of pollution of the latter. It appears to find
its way into the Channel above the 133 mile point, probably
somewhere about the 10} mile point, in its most concentrated
condition at low water.
MetruHops oF BacTERIOLOGICAL EXAMINATION.
Two samples were collected in the early morning of
November 3rd, 1921, from the respective areas, packed in sterile
air-tight tins, and brought to Liverpool immediately after
collection. The Church Scar sample was examined the same
afternoon. The North Wall sample was packed in ice and
dealt with the following morning, November 4th. The usual
procedure was followed, viz.: an emulsion of five mussels in
250 c.c. of sterile water, giving a proportion of one mussel in
50 ¢.c., or one-fiftieth of a mussel in | c.c. was made. One
c.c. of this diluted emulsion was plated in MacConkey’s Bile
Salt Neutral-red Lactose Agar, five plates being made, and
these were incubated at 37° C. for 24 hours. In addition, four
tubes of Bile Salt lactose litmus broth were inoculated as
follows. From the original emulsion of five mussels in 250 c.c.
of sterile water, 1 ¢.c. was taken and put into 100 ¢.c. of sterile
water. This was called Dilution I., and each ¢.c. contained the
equivalent of =jth part of a mussel.
From Dilution I., | ¢.c. was taken and put into another
100 c.e. of sterile water. This was called Dilution Il., and
. 1
each ¢.c. contained i 0th part of a mussel.
From Dilution IT, 1 ¢.c. was taken and put into 100 c.c.
of sterile water and called dilution ITI., and each e.c. contained
1 «
soo000000h part of a mussel.
From Dilution III., 1 ¢.c. was taken and put into 100 c¢.c.
of sterile water and called Dilution LV., and each ¢.c. contained
1
& 000,000,000 part of a mussel.
Thus, four dilutions were made, each succeeding one
being 100 times more dilute than its predecessor. From each
Dilution I[., I1., III. and IV., 10 ¢.c. were taken and put into
four tubes respectively of Bile Salt, lactose, litmus broth
and incubated at 37° C. Thus it will be seen that the quantity
of mussel in each tube was jth in L., sath in LH., synth in
(NEE, chaal saeeinan LY
It is not considered necessary to give details of sterilisa-
tion, except that all the usual precautions were observed.
After 24 and 48 hours’ incubation at 37° C., the plates were
counted, with the following results :-—
Church Sear.
I.—24 hrs. 7 white, 83 smallred, 0 large red colonies.
ASh LOO) 130 35 Gyre.
32
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V.—24 ,,
48 ,, was not counted. General fusion of colonies.
In the above results the round white colonies varied from
approximately ;5th” to gth” in diameter, the small red from
approximately 34nd” to 75th”, and the large red from kth”
to th’. Some of the large red colonies tended towards a
paler shade, almost a pink, while the small red were a deep
red surrounded by a rosy halation. The white colonies
without exception had a small red centre. After 24 hours’
incubation, the plates showed a large number of microscopic
red points, which resolved themselves into the usual small
red colonies. The results of incubation of the Bile Salt
lactose litmus broth were as follows :—
I.—This tube after 24 hours showed an acid re-
action and was gassing freely. This contained ~4,th
part of a mussel.
II.—This tube after 48 hours showed a slight acid
reaction, but no further change after prolonged in-
5 . . 1
cubation. This tube contained x oth part of a mussel.
IIT. and IV. showed no reaction, even after pro-
longed incubation.
As a result of these tests and the consequent evidence of
the presence of the Bacillus coli group of organisms, it was
decided to submit several colonies for detailed examination.
This was very kindly carried out by Mr. Smith, of the Bacterio-
logical Department in the School of Pathology, whose report
is embodied in this one. He examined a plate of each sample,
on which white colonies were numerous. These were regarded
as significant of recent pollution, and were subcultured with
the following results :—Lactose A, Saccherose +, Glucose +,
Mannite +, Maltose +, Indol —, Motility +; A = Acid, + =
acid and gas, — = no reaction. The organisms were identified
as Friedlander’s Pneumobacillus. No organisms of known
pathogenicity were found. The relative proportions of
occurrence of the different organisms studied were Pneumo-
bacillus Friedlander +, B. Coli + + +, Streptococci + +.
The most significant of these results is the relative abun-
dance of Streptococci. This organism exists in large numbers
in human feeces, and its association with other fecal bacilli
not only indicates serious, but also recent, pollution as it
is a delicate organism and only survives for a short time when
isolated.
North Training Wall. 15} miles from Preston Docks.
+
No. 2 Gas Buoy.
1.—24 hrs. 0 white, 100 small red, 0 large red colonies.
[ids a oD if ee co
fpeton SG? tae BERD ir pe Ps "
IV.—24 ,, Quits O70) = 16 a a
V.—24 ,, 5 ,, This plate was sent to Bacteriological
Department and not counted, but
contained a large number of small red
colonies.
VI.—24 ,; | uae 177 small red, 2 large red colonies.
After 48 hours a great many more microscopic red colonies
became visible, in addition to those already counted, so that
these counts only represent the minimum number of organisms
present. The small colonies which were counted were those
easily visible to the unaided eye, and were mostly about 7;th”
in diameter or less, and were well scattered.
Result of Incubation in Bile Salt Lactose Litmus Broth :—
Four tubes were inoculated as before, with the following
results :—
Tube I., after 24 hours’ incubation, showed an
acid reaction but no gas formation, but after 48 hours
was gassing freely. There was no reaction in Tubes
II., III. and IV. after 48 hours.
These four tubes were incubated for a long period,
but no further reactions were observed.
The result of the examination of the suspected white
colonies on Plate V. by Mr. Smith was as follows :—Lactose
A, Mannite A, Maltose A, Indol +, Motility +. A= acid
production. An agglutination test against Bacillus typhosus
and Bacillus dysenterie was carried out with negative results.
The organism examined was identified as Bacillus pyogenes
fetidus. Other bacilli present were Bacillus coli and Strepto-
coccus. No organism of known pathogenicity was found.
Here again is evidence of fecal pollution, but of a different
character from the Church Scar sample. The main feature
is the relative abundance of lactose-fermenters and the absence
of non-lactose fermenters.
Comparison of the two Samples.
In comparing the two samples, the following explanations
should be carefully noted. The average number of organisms
per mussel in the Church Scar sample is estimated from four
plates after 48 hours’ incubation. The fifth plate was dis-
carded owing to a general fusion of the colonies in the centre,
10
thus rendering a count of no value. The count after 24 hours
is shown. In the North Training Wall the average number
of organisms per mussel is estimated from five plates after
24 hours incubation. After 48 hours the increase in the
number of colonies was very considerable, but these were all
microscopic ; consequently, it was decided not to count them ;
so the estimation shows the minimum organisms per mussel.
Average numbers of organisms of different categories
found per mussel :—
N. Training
Church Sear. Wall.
24 hrs. 48 hrs. 94 hrs.
Lactose fermenters—
Small colonies ... 4,662 ...11,500 ... 16,200
Large Colonies ... 162... 425 ... 240
Lactose non-fermenters 275 ... 425 1... 10
Acid and gas were produced in lactose, bile salt, litmus
: . . 1
broth in =3,th part of a mussel, and acid only in jyoth part
of a mussel in the case of the Church Scar sample.
Acid and gas were similarly produced in 535th part of a
. . 1 .
mussel, but no reaction was observed in sp.th part in the case
of the Training Wall sample.
CONCLUSIONS.
Church Scar.—There is evidence of recent fecal pollution
borne out by topographical evidence, and particularly by the
presence of Streptococci in relative abundance. The presence
. . "WW: . 1
of acid forming bacilli was detected in sooth part of a mussel.
North Training Wall.—The pollution here appears to be
of a more diffuse nature. There are more lactose fermenting
bacilli and fewer non-lactose fermenting organisms than in
the Church Scar sample. Topographical evidence would
suggest that sewage bacilli have to undergo a longer period of
isolation from their normal habitat than those reaching
Church Scar. This may have resulted in a natural selection
11
in the course of which bacillus coli remains, while the less
resistant non-lactose fermenters are eliminated. Probably
at the late ebb and early flood the water is highly infected with
bacillus coli, so that these mussels may always contain a large
number of this organism. The presence of streptococci
suggests a recent fecal pollution. The nearest point of
infection would be the point referred to at the ten-and-a-halt
mile mark (three miles away) where the Lytham and Ansdell
sewers ultimately discharge into the Channel. The presence
of streptococci seems to indicate, therefore, that the Training
Wall beds are little better than those at Church Scar. The
significance of the presence of Friedlander’s Baeillus and
Bacillus pyogenes fetidus in the Church Sear and Training
Wall samples respectively is not discussed. Conclusions as to
the degree of pollution are best based on the occurrence of
bacillus coli and streptococci.
Before concluding this report, thanks are expressed to the
Ribble Navigation Committee and to Mr. Cochrane, the
Assistant Engineer, for the invaluable assistance given.
Without his help it would have been a most unsatisfactory
undertaking, if not impossible. The Engineer's launch, the
* Aid,’ was placed at our disposal on the two occasions these
beds were visited, thus enabling a wide area to be examined
while uncovered by the tide in a minimum of time.
It is, perhaps, not out of place to report on the value of
mussels to an undertaking like the Ribble Training Walls.
The intention is to make Preston a seaport town, and to
accomplish this it has been necessary to dredge a deep channel
as far as the deep water, some 14 to 16 miles away. To
ensure the permanence of this channel, each bank has been
reinforced with rubble practically all the way from the Docks.
The constant danger is the washing away of the walls, as they
are only loose stones and easily dislodged by strong tide.
12
The mussels, however, accumulating in large numbers on
these walls, form a fine natural binding material, and are
regarded vory favourably by engineers in charge of this
work.
OBSERVATIONS ON THE ABOVE REPORT.
By Professor J. Johnstone, D.Sc.
It is not any easier to give practical interpretation to the
above report than to any others made on the local shellfish
layings. So far as I know, nothing has happened lately that
tends to cast strong suspicions on the mussels taken from the
Ribble Training Walls, and in the absence of such strong
suspicions the bacteriological evidence produced does not
seem to me to justify any restrictive measures. It must be
noted that some degree of bacterial pollution must be expected
in all the mussels taken from such a foreshore as that of
Lancashire. Considering everything, it may be safely con-
cluded that some degree of pollution may reasonably be
neglected. What then are we to understand by ~ some.”
There has been no official ruling or utterance on this point,
either by the Public Health or the Fisheries Central Authori-
ties, and until this has been made it is unsafe to base any
recommendations as to restrictive action on bacteriological
evidence alone.
This caution is all the more necessary since we know that
mussels may be exposed to notable contamination after they
have been “* removed from the fishery ” and are being handled
on their way to the consumer ; evidence that this may be the
case was produced at a public enquiry into the contamination
of mussels from the localities mentioned in this report. The
case for action (if any) ought rather to rest on the topographical
and epidemiological evidence—that has been the general
opinion—so far as there has been any general agreement on
the matter.
13
I have seen these localities myself and have made
analyses (which agree as well as can be expected with those
made by Mr. Birtwistle). I found in 1913 a mean of 21,000
organisms per mussel from samples taken from the Training
Wall. and 19,000 per mussel from a sample taken from Church
Scar in 1916. The conditions that may be seen in the Channel
adjacent to the Training Wall do not suggest pollution at
all; the water, and the banks, &c., exposed on the ebb tide
look clean and healthy, and this was also the opinion expressed
by Mr. Scott, who has had very much experience of this kind
and is a highly competent judge. The Royal Commissioners
on Sewage Disposal say much the same thing. ~* Our general
impression,’ they wrote, ~ of the whole Ribble Estuary was
very favourable. In spite of the extensive and populous
district draining into it, and the varied industries contributing
their trade effluents, no marked indications [of sewage] are
to be found, even a few miles below Preston, while at Lytham
all signs have disappeared.” (Rept. V., App. VI. ed 4284,
1908.)
}
But the impression that one obtains by personally
examining Church Scar is different. There is evidence of
recent and immediate sewage pollution; there are privies
actually discharging on the Scar itself, and there are two large
outfalls of crude sewage about a mile and a quarter away from
the centre of the mussel bed. The latter may smell offensively,
and in addition to all that, there is the general pollution of
the Ribble. Whatever value the fishery on Church Scar may
have cannot be much, but much or little, it seems reasonable
to urge that mussels taken from this bed should certainly not
be marketed for human consumption without being relaid,
or otherwise purified. If that is impossible, then the fishery
had better be prohibited.
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