a = a _ 5 “ AL is Aa | / . = 7 . eau ne : Aa @ aye 4 - =a a ee ey ws <2 gee = * t Pre aes fa tes \jahu Lee Cee, J 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 ‘saaano Aouonbedf pozeEpnopeg | | 7-666 | 1Z> | 8-666 | ¥90°C| 0-000I | EFE‘T| 9-666 | ELI‘L| 6-000T | 1LL‘9| T-eL6 | ezL‘F| 6886 | eee'e| zF86 | ZOLF LO I ¥:0 T £0 ie 9-0 Gc eee | eee L-0 1 wee see eee eee G-Le L-0 Ll | #2 G | #0 z ea ener IT | 30 € see Tile Ae i gescmellbites a lemeage eB peg L | 6-0 ¢ | 60 Lb | &0 9 | &0 z sn tas gS nee Uae eters ze AzOre Netgen || 8-0 6 | eT or | 2-0 = | £0 6 io =a ys | ope L-0 T -|ser | or | 81 Ol | 9% 6r | TT ie ec0 Ce \eLO) aula | el elaiee 5 oa G&S SF L-¥ 9G 6-1 FI GG €1 8-0 ¢ GO I L-0 G G-6E 7 ad FE IL i al | BG GG 9€ 6 0G Tel i €-0 € £0 | $ GHOé <9 sa 1-SP €6 9-¢ 1é Gas GG 8-9 Sf 9-T € F0 |G F:0 G G-0€ GT G L-9F C6 FEL FL FFI FOL 9-11 €L EG v 6:0 9 Gol € G66 L-0 I 6-6F 601 9-CT | 68 G LT 9E1 0-61 8ST 8-€ él GT | € GS FI G-8G GP 9 8°87 IOI L-91 66 9-FG | LLI 9-6Z CCG 6G LI GG ) 8) UP 8I GLE L-9 6 VSP OOT L1é | OGT GLE | L6T LP 1S€ F6 8 GP | I €-8 FE G-9G 6-F1 0G 8-0¢ SOT L-€€ LOT GI1é EGE 1-29 99€ FST €¢ (oz | PG C1 IL GCG €-GG 0& L:8& 08 | 8-8€& FIG 6-9§ G9 9-28 G9G GGG FIl GF 6¢ 6-LZ Té1 GG 8-6 CE L:09 FEL 1-6¢ 9ZE GC: OF 88 8-LOL 119 GF 1G £96 | 601 8-8F CPG G-€¢6 9-0G 89 L-69 PFI VOL | 1@P L19 SEP 0-LTT LIL 9-69 GIF VPP | 961 G-08 LOP GGG L8G 6L 8:L9 OFT S-9IL | #19 | 9-69 | 66F €-ZEL | 9F8 0-O1T FE9 8-FL €8E €O1l TFS GIG LOL G6 PSL GOT 6-FI1 ee9 «8 O19 8-LIT OL8 98ST | €08 8-LII 81g 98ST G89 G-0G 6-9 Gs GEL ISI €-0€T SIL 9-9L OSS LTOT 89L L161 L68 6-991 109 8-PLI $98 G61 FS01 6€T G-9OL 8ST 8-02I 999 8-16 6¢9 9-91 OS 9-ELT 8éL T-S6I GLL 0-SST 9GL G-8T F691 FIG FP9 €é1 G-68 | €6F L:SIL | 6&8 L-0¢ 16G L-€0r 60F L-PLI 199 G-LOL 667 GLI L- LOG 6LE L-69 6cl | L&6 | 91S 8-OFL | OLOT| 9-82 6ST 6-1F 8GE G- LOT OLD FP LG 9G G-9T 0-0FT 881 €-16 Fr | OEE | L8T | S-66 | FIL G-E1 96 O-EL C6 FOF | imal €-61 raul GGT 6:6¢ Ik a 2 | € | ¥:0 1G | €:9€ | 096 @eg 9¢ LS 6€ 0-6 | GF ¥8 6€ GF 9-6I LI F0 I | 6:0 +S | LG | IP 9-T LI L-0 G tell 8 GG OT GET GT G as i G0 Il | TT 8 F-0 lee G0 G 1-0 — L-0 8 GEL 1-0 I sto vee | ees | 2.9 Pe L-0 lots S06 eae a0 |Z e eT Paled Hy ale dh ooeae fh ee if oe of | f a Sa £ eee | if ie any i ae | ee “yy 3u9T “Iequ1900(T ‘IOQUIDAON =| “1q.0900) ‘loquteydag ‘qsnsny ‘Ane ‘aune “LV uvoyl "EL61-806L “Asenjsy Aosuaiy YO “IA 21geL (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. 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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 — — D> | & _— = Jo be | oe s. |< a | 8 — — = | & | 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 = Sate Nee — = ! | i l | » G3 res ea 1 1 | | | | | eee leas | 5 | i 1 eee | 2 Pak 1 Bed) es | | 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 AG a “GEBL ST TG) Cs xUehe a ce licn ‘aq urRdaIO]Y “CEBI ‘T “ 204 IDABLE NO Ne — he. "1261 ‘¢ “sue | TW RAAN ils | 10d Arey "IZzR °e *xuryy SON Sst : 2 t~ PO eee ore yan cenenre ‘OZG6T “6 ‘XURTT iaais | & ee = “SI6L ‘syTeuts | ‘OZ6T “6 ‘XURT oan i 16 Ears lie ; CEG ‘T “USTOAA "OZ61 ‘O*xuvyy | ~~ dons 2 fag = 7 : ; “TZ61 “ZT “USTOM “OZ6T “9 Sxuryy ey eee crucial ee a = ‘Tz ‘oT ‘usta, ann See te IG6L “OT “ASO MA dT OL XUeyy oe CA eal | Yo! FIGI G ‘xUryy rHodt : | FIGT “USIOM ° HOO 6 le :c “Ysa, FIGT ‘8 xURY icile cla ta deere b= €16T YSTP A "FIGL ‘2 SxURTY PRSSaN |S FIGT ‘9 ‘xueyy Fee eases hid ty Jo osURYy ee Ine) “VW Jo onuey ouise ay ee SS 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. Biq. 6. ma) oy ea Ie “ | i fe A eT al Yot *. 4! P| - a | - Lee _ meee rane ise - : - Bad 5 yan uy Fieehey rr hee Onn | onl fis bad b) tee 4 efi Tabet a ver ee oS} 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 I1.—24 ,, Tete 90 *; 3 99 29 48 ,, Si) 260 “ 6 » » PET 240 13,) 9 Gar» 100 3 6 35 PA £518. EZ i ge S00 sS 16 » » PVH 24 2 43 LOO a + e > 48550 V4 in e230. i 12 H » 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. e st. 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