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FINLAND

by

Outi Heikinheimo-Schmid, Markku Pursiainen, Kai Westman,
Pekka Tuunainen and Aimo Järvinen 1

Introduction

Finland's inland waters cover 31 000 km2, which is about 9.4 % of the country's total area. There are over 60 000 lakes, 17 of which have a surface area of more than 200 km2 each. The lakes are shallow, the average depth being 7 m; their total volume is 220 km3. Together they have a total shore length of 130 000 km. Nearly one hectare of lake area and about 30 m of shoreline are available per capita of the population (4.9 million in 1984). The total length of the rivers exceeds 20 000 km.

The new fishing law (1983) expanded fisheries administration to include eleven districts, each headed by a fisheries biologist. Each district is divided into uniform fishing areas in order to facilitate regional planning of the fisheries and their management.

In 1984 some 541 000 people were engaged in fishing in inland waters. About 2 500 of them were professional or semiprofessional fishermen and the rest fished for recreation and their own use.

The total catch from inland waters was estimated at about 30 000 tons in 1984. This was about 20 % of the total catch for the country (Appendix 1).

The commercial catch in 1984 was 5 400 tons (Appendix 1). The main species in the catch are perch, pike, vendace and roach.

Damming of rivers and water level regulation of lakes and reservoirs, mainly for hydro-electric power generation, have created severe problems in fisheries management. Due to extensive water protection measures, pollution of waters has strongly diminished. About 130 km2 of the lake area in Finland, i.e. 0.4 %, is badly polluted by industry or sewage, and in 20 % of the lake area the water quality is classified at satisfactory or passable.

Extensive fish stocking programs form the main part of the management of economically important fish stocks. The total number of fish released in 1984 was 45 million (excluding newly hatched fish), more than 75 % of these were whitefish. During 1982–1984 the number of fish used for stocking rose by nearly 30 %, mainly due to increased whiteüfish stocking (Appendix 2).

Production of rainbow trout for human consumption has grown by 50 % since 1982, being 9 500 tons in 1984 (Appendix 2 ).

The EIFAC National Committee, chaired by the EIFAC correspondent for Finland, is responsible for liaison between EIFAC and Finland and works on subjects of current interest to EIFAC.

1 Finnish Game and Fisheries Research Institute, Fisheries Division, P.O. Box 193, SF-00131 Helsinki 13, Finland.

I FISHERIES BIOLOGY AND MANAGEMENT

1. Economic aspects of commercial and recreational fisheries

In 1984, the value of the total catch from inland waters (30 000 tons) was 183 million FIM (30 million USD). This was 43 % of the value of the total catch in Finland in the same year.

The value of the total catch from inland waters taken by professional fishermen (5 400 tons) was 33.2 million FIM (5.5 million USD) in 1984, two thirds of which was due to the vendace catch.

Vendace is the most important fish species in the catch of the commercial fishery in inland waters, with annual catches of about 4 000 tons during the 1980s. As regards other species, the Lokka and Porttipahta reservoirs in northern Finland have become to remarkable professional fishing areas for e.g. whitefish and pike.

The annual profitability of commercial fisheries is studied by means of daily records kept by some 70 fishing households or enterprises in inland waters.

A study on the use of the professional fish catch was published in 1984. About half of the domestic fish used as human food is processed, but the fish from inland waters is mostly used fresh. The proportion of inland fish used as animal feed is insignificant (62).

Subsistence and recreational fishing is of great economic and social significance in Finland. Perch and pike are the most important species in the catch of subsistence and recreational fishermen. More than half of the catch is taken with gill nets. In 1984, the value of the catch (24 400 tons) was 149 million FIM (25 million USD).

A personal fishing licence (19 FIM from 1.1.1985) and the permission of the water owner are generally required for every kind of fishing, but district licences enable angling with natural bait and ice fishing with rods without the permission of the water owner.

In 1984, the annual catch of the native crayfish (Astacus astacus) was estimated at about 2.5 million individuals, the value of which was 17.5 million FIM (2.9 million USD).

The inquiry concerning subsistence and recreational fishing made in 1984 will give the first more accurate estimate of the crayfish catch, because in 1983 a general fishing licence became obligatory for crayfish fishing as well.

The lamprey catch in 1983 was 2.3–2.4 million individuals, which is about 100 tons. The value of the catch was estimated at 4.3 million FIM (800 000 USD).

The number in brackets (   ) refers to the number in the bibliography.

2. Survey and appraisal of inland waters

So far fish stock assessments have been published from eight Finnish lakes and the coastal area, the main species assessed being vendace, whitefish, perch and pike. In five lakes studies were continued on the population dynamics and causes of year class fluctuations in the vendace (Coregonus albula), which is the most important species for the commercial fisheries in lakes. A research program was continued by the University of Turku with the support of the Academy of Finland, on the ecosystem in Lake Pyhäjärvi, Säkylä, which is the most productive vendace lake in Finland (annual catch 20–40 kg/ha). A study on the present state of the fisheries in Lake Saimaa, East Finland, was published in 1984 (51).

The echocounting method for estimating fish numbers, developed within EIFAC, has been used in seven lakes in Finland during 1984 and 1985. Finland also participated in the echocounting experiment on Lake Tegel, which was a part of the EIFAC program, International Intercalibration Exercise on Fish Sampling Methods in Lakes.

During the intersessional period, extensive research programs for planning regional fisheries management have been in progress. The report on a three-year investigation of the fisheries system in Lake Oulujärvi was published in 1985 (52, 53).

3. Management of inland waters

3.1 Restoration of waters

Restorative measures have been carried out in about 30 rivers in order to increase fish and crayfish production and improve the fisheries. At the same time follow-up research programs have been continued, to study the results of the restorations.

3.2 Stocking

Fish stocking is the most common management method used in Finland. In 1984 the number of salmonids (Salmo and Salvelinus sp.) released at the age of one summer or more was 6.3 million. The corresponding number for whitefish species (Coregonus sp.) in 1984 was 34.8 million and for other fish and crayfish species 4.0 million. These last two groups are mostly stocked as 1-summer-old fingerlings (See also Appendix 2). It has lately been estimated that the value of the yearly input of whitefish, salmon and brown trout is about 40 million FIM (7 million USD). This stocking gives a yearly catch of 3.5 million kg of these fish species. The value of the catch is about 80 million FIM (13 million USD), i.e. about double the value of the stockings.

A number of transfer stockings have also been done with some fish species other than those mentioned in Appendix 2 and also with crayfish (Astacus astacus) and lamprey (Lampetra fluviatilis).

3.3 Marking and tagging

To evaluate the stocking results, and for research purposes, some 87 500 salmonids were tagged with Carlin tags in 1984 and about 125 200 in 1985. The corresponding numbers for other fish are 10 400 and 4 800. In addition, about 311 500 salmonids and 578 200 other fish, mostly whitefish, were marked with microtags (“nose tags”) in the two years.

The Finnish Game and Fisheries Research Institute handles all the returns of Finnish tags. Computers are used to store the data, deal with correspondence and payment orders, and compute the tagging results (yield, etc.). The number of tags handled annually is around 10 000. In 1985 the recovery register contained 75 000 records.

3.4 Introductions

No new fish or crayfish species were introduced into Finland during 1984–1985. Elver introductions will propably begin in 1986, which means that the continuously decreasing eel catch may be expected to improve in future years. Before introduction the elvers will be kept in quarantine, to prevent the spread of fish diseases.

4. Research programs shared with other countries

Cooperation has been continued between Finland and the neighbouring countries. In the Tenojoki (Tana) River on the Finnish-Norwegian border, the yearly studies on the Atlantic salmon (Salmo salar) stock include preparation of catch statistics, catch sampling, and assessments of parr densities. In 1984, the joint studies on salmon were extended to the Näätämöjoki (Neiden) River.

The Finnish-Soviet Border Water Commission has continued its work on questions concerning the fisheries of the waters in the border region, chiefly Lake Inari and Lake Pyhäjärvi (Karelia). In Lake Pyhäjärvi, comparisons were made between the fish stocks on the Finnish side, which are under heavy and constant fishing pressure, and those in the Soviet area, where fishing pressure is insignificant. A final report on the results from Lake Pyhäjärvi will be given in 1986, and monitoring will continue. Finnish-Soviet cooperation was continued in investigations on salmonid smolt production in Finnish and Soviet Karelian rivers. Finland also participates in the research program on Lake Säämäjärvi and the Rybinsk Reservoir in the Volga River, in which echocounting is used.

Research on the fish stocks and fisheries in the Tornionjoki (Torneå) River was continued in cooperation with the Finnish-Swedish Border River Commission and the Swedish fisheries authorities. A report on the Finnish investigations was published in 1985 (38).

Liaison has been continued with inland fisheries researchers in Poland, the main subjects being fish culture, and research on whitefish, vendace and sea trout.

5. Other subjects

The report of the Working Group on Enhancement of Migrating Fish Stocks was given in 1985. The foremost measures should be construction and improvment of suitable habitats for migrating fish. The working group gave a list of the areas which need restoration, ranked in order of urgency, and both short-term and long-term programs for restoration measures (59).

II FISH CULTURE AND DISEASES

1. Fish culture

1.1 Fish farms and the production

The rainbow trout is practically the only fish species farmed for food in Finland. In 1984, 335 farms produced 9 500 tons of fish for human consumption. More than half the total amount is produced in brackish water in net cages (See Appendix 2).

Fish for stocking purposes are reared either by intensive methods in artificial tanks or earth ponds (mostly salmonids) or by extensive methods in large ponds with a natural food supply. Many of the farms that produce rainbow trout also produce other salmonids for stocking. In 1984, the number of salmonids produced for stocking purposes, excluding newly hatched juveniles, was 6.3 million (41 % for inland waters). The total area of the natural-food ponds in that year was 8 500 hectares and their production was 38.7 million (Appendix 2).

In 1984, the state fish farms (10 in operation and 4 in the construction and planning phase) belonging to the Finnish Game and Fisheries Research Institute produced some 139 million whitefish eggs, 11 million salmon eggs, 16.2 million brown trout eggs and 1.0 million char eggs for rearing juveniles for stocking. The production of pike-perch fry increased rapidly in the 1980s, exceeding 6 million in 1985.

1.2 Economic evaluation of aquaculture

If producer prices are used, the total value of the aquaculture products in 1984 was 269 million FIM (45 million USD), of which 204 million FIM (34 million USD) consists of rainbow trout for human consumption and the rest of stocking material. Since 1982 the value of aquacultural products has increased by over 60 %.

1.3 Fish nutrition research

The dry fish feeds used in 1984 amounted to almost 23 000 tons. Low value fish and Baltic herring form a fairly important part of the fish feeds, especially in brackish-water net-cage farming.

Fish feed development is continuously researched in cooperation with feed producers and farmers. The main goals are to improve fish growth and feed conversion, to reduce the waste nutrients originating from feeds, and to examine the effects of the feeds on the quality of fish for human consumption and on the quality of stocking material. New types of fish feeds are also needed for intensive cultivation of non-salmonid species.

1.4 Development of aquaculture technology

In recent years the research in aquaculture technology has concentrated on comparative testing of the physiology of stocking material reared under different conditions. The main factors examined at the fish farms have been rearing basin shape and current conditions, feeding technology (development of automatic feeders and feeder processors), illumination and use of warm water and heated effluents.

To avoid selection caused by cultivation from generation to generation, brood stocks are primarily based on the natural spawn of known native or released fish stocks. On the other hand, a rainbow trout breeding program has already been planned and a new fish farm will be built especially for this purpose (55).

The problems caused by long distances between fish farms and stocking sites are nowadays partly avoided by better transportation techniques and by using release ponds in the most important stocking sites. In these ponds or basins, fish are able to recover safely from transportation before they are released (39).

2. Fish and crayfish diseases

The official fish health programme maintained by the National Veterinary Institute has continued, and by the end of 1985 the number of fish farms belonging to it has risen to 117.

Vaccination has significantly reduced outbreaks of vibriosis (Vibrio anquillarum) and the need for antibiotics in 1984–1985, in spite of the large increase in fish farming production. However, outbreaks of contagious dermatitis (Aeromonas salmonicida var. achromogenes) are occurring increasingly frequently in coastal rainbow trout farms.

Two pathogens were recognized for the first time in Finland in 1984. The virus for IPN (infectious pancreatic necrosis) was isolated from a one-year-old rainbow trout suffering from vibriosis on the southern coast. However, no clinical symptoms specific to the infection could be observed. A mild outbreak of enteric redmouth disease (Yersinia ruckeri) was diagnosed in salmon and whitefish in northern Finland and caused some mortality (50).

In natural fish stocks, lymphoma of pike is the most prevalent disease in coastal waters. The information accumulated indicates that the prevalence is not connected with pollution but is highest in areas where the pike is living at the extreme limit of its salinity tolerance.

Some new cases of crayfish plague appeared in 1984–1985. Research on plague resistant signal crayfish as plague spreaders has continued. In fact, under culture conditions, juvenile signal crayfish have shown rather high plague mortality. Haemolymph studies on Aphanomyces -infected crayfish and signal crayfish have continued (17).

The number of finds of the parasite Psorospermium haeckeli has risen to five in southern Finland. The haemolymph values of infected crayfish are under study.

III FISH AND POLLUTED WATER

1. Fish farm effluents

The most serious factor limiting the expansion of aquaculture in Finland is the eutrophication caused by the fish farm effluents, especially the phosphorus. The total phosphorus loading from fish farms in 1982 is calculated to be 90 tons. For comparison, the phosphorus load originating from industrial waste waters is 644 tons a year.

An effective method of reducing the amount of waste phosphorus is to minimize the phosphorus content of the dry feeds. At its best, the present level is about 0.9 %. Removal of waste solids by using self-purifying rearing basins and a whirling separator gives a further marked reduction of waste phosphorus. Even better results can be achieved by using industrial sieving equipment and flotation, but this method is rather expensive at present.

2. Biological monitoring

Toxicological and physiological methods of evaluating the effects of effluents on fish at different stages of development are available for administrative use. Biological monitoring is playing an increasing role in environmental protection in Finland.

Standard national methods are available for using fish and the cladoceran Daphnia in acute toxicity testing. Long-term toxicity testing methods are being delevoped.

Water quality criteria have been prepared for fishing waters and will be evaluated over a period of some years.

International cooperation with the Helsinki Commission, ICES and OECD continues in this field.

3. Bioaccumulation of toxic substances in fish

A national program for monitoring the concentrations of chlorinated hydrocarbons and heavy metals in fish has been in progress since 1978. More is now known about the presence of chlordanes, toxaphenes and polychlorinated dioxines and dibenzofuranes in fish. Extensive research carried out during the last three years has revealed that air-borne pollutants may be the main reason for the high mercury concentrations in fish in waters unaffected by discharge of wastes.

Although the direct release of mercury into the water has been greatly reduced since the late 1960s, the mercury contents in fish are still a severe problem in Finland. In almost half of the Finnish lakes the mean mercury concentration of predatory fish (pike and burbot) exceeds 0.5 mg/kg, which means that consumption of these fish should not exceed 0.5 kg/week (27, 61).

4. Acidification of inland waters

At the beginning of 1985 the Finnish government initiated a 5-year research project on acidification due to air pollution. The fisheries part of this project is conducted by the Finnish Game and Fisheries Research Institute in cooperation with the University of Helsinki. Data on fish populations and water quality were collected from 75 small lakes in different parts of Finland. According to preliminary results, the fish populations of several small acidified lakes in the southern coastal area of the country are sparse. The effects of acidification on fish, including the effects of heavy metals in precipitation, are being examined in both laboratory and field experiments, special attention being paid to the reproduction of fish (46, 47).

5. Physical habitat modification

Methods have been developed for evaluating the effects of habitat modification on fish stocks and the results of management measures. In 1985, guidelines were published in order to unify the procedures (7, 37, 70).

In 1984 a report was published on a three-year research program concerning the effects of the dredging and land-drainage in the Kyrönjoki River on the fish and crayfish stocks and the fisheries in the river estuary and in the sea area outside the river mouth (9, 15, 40).

Acknowledgements

The information for this country report was obtained from the members of the EIFAC National Committee for Finland and many other specialists in different fields. We wish to thank all of them for their contribution, and Mrs. A. Damström for checking the English language.

SELECTED LITERATURE

  1. Ankeriastyöryhmän mietintö (Report of the working group on eels). Helsinki. Maa- ja metsätalousministeriö. Työryhmämuistio MMM 1984:26. 26 p.

  2. BENGTSSON, Å. & MIETTINEN, V. 1985. Spinal deformities and concentrations of heavy metals and chlorophenols in fourhorn sculpin (Myoxocephalus quadricornis L.) of the Finnish coast of the Gulf of Bothnia. Helsinki. Publications of the Water Research Institute. (in press)

  3. BUSHNELL, P.G., NIKINMAA, M. & OIKARI, A. 1985. Metabolic effects of dehydroabietic acid on rainbow trout erythrocytes. Comp. Biochem. Physiol. 81C, p. 391–394.

  4. ELORANTA, A. 1985. Grayling (Thymallus thymallus (L.)) in lower part of the Rautalampi watercourse, Finnish Lake Disrict. Verh. Internat. Verein. Limnol. 22, p. 2555–2559.

  5. HAKKARI, L. & BAGGE, P. 1985. On the fry densities of the pike (Esox lucius L.) in Lake Saimaa, Finland. Verh. Internat. Verein. Limnol. 22, p. 2560–2565.

  6. HILDEN, M. & KETTUNEN, J. 1985. Models for the assessment of environmental impacts on fish populations and fisheries. Finnish Fish. Res. 6. (in press)

  7. HILDEN, M., LEHTONEN, H., IKONEN, E. & SALOJÄRVI, K. 1985. Tutkimusmenetelmät kalataloudellisessa velvoitetarkkailussa (Research procedures in determination of compensation for damage to fisheries). Helsinki. RKTL, kalantutkimusosasto. Monistettuja julkaisuja 33, p. 1–187.

  8. HOLOPAINEN, I.J. & PITKÄNEN, A. 1985. Population size and structure of crucian carp (Carassius carassius (L.)) in two small, natural ponds in Eastern Finland. Ann. Zool. Fennici 22, p. 397–406.

  9. HUDD, R., HILDEN, M., URHO, L., AXELL, M-B. & JÅFS, L-A. 1984. Kyrönjoen suisto- ja vaikutusalueen kalatalousselvitys 1980–1982 (Study of the fisheries of the Kyrönjoki River estuary). Helsinki. Vesihallitus, tiedotus 242 A. 275 p.

  10. HUNER, J.V., KÖNÖNEN, H. & LINDQVIST, O.V. 1985. Responses of intermolt noble crayfish, Astacus astacus (Decapoda, Astacidae), to short-term and long-term holding conditions at low temperature. Aquaculture 47, p. 213–221.

  11. HUNER, J.V. & LINDQVIST, O.V. 1984. Effects of temperature and diet on reproductively active male noble crayfish (Astacus astacus) subjected to bilateral eyestalk ablation. J. World Maricult. Soc. 15, p. 138–141.

  12. HUNER, J.V. & LINDQVIST, O.V. 1985. Exoskeleton mineralization in Astacid and Cambarid crayfishes (Decapoda, Crustacea). Comp. Biochem. Physiol. 80A(4), p. 515–521.

  13. HÄNNINEN, O., KOIVUSAARI, U. & LINDSTRÖM-SEPPÄ, P. 1984. Bio-transformation, especially glucuronidation and their control by temperature in fish. In: Advances in glucuronide conjugation. Ed. S. Matern, K.W. Bock & W. Gerok. p. 101–107.

  14. HÄNNINEN, O., LINDSTRÖM-SEPPÄ, P., KOIVUSAARI, U., VÄISÄNEN, M., JULKUNEN, A. & JUVONEN, R. 1984. Glucuronidation and glucosidation in aquatic species in boreal regions. Biochem. Soc. Transactions 12, p. 13–17.

  15. IKONEN, E., AUVINEN, H., KUITTINEN, E. & HÄSTBACKA, H. 1984. Kyrönjoen nahkiais- ja vaelluskalakantojen tila (Condition of lamprey and migratory fish stocks in the Kyrönjoki River). Helsinki. Vesihallitus, tiedotus 247 A, p.1–32.

  16. JURVELIUS, J., LINDEM, T. & LOUHIMO, J. 1984. The number of pelagic fish in Lake Paasivesi, Finland, monitored by hydroacoustic methods. Fish. Res. 2, p. 273–283.

  17. JÄRVENPÄÄ, T. NYLUND, V., RAILO, E. & WESTMAN, K. 1985. The effects of the crayfish plague fungus Aphanomyces astaci on the haemolymph of Astacus astacus and Pacifastacus leniusculus. In: Freshwater crayfish 6. Ed. P. Brinck. Lund. (in press)

  18. KOIVUSAARI, U. 1984. Xenobiotic biotransformation in rainbow trout, Salmo gairdneri, with special reference to seasons and reproduction. Thesis. Publications of the University of Kuopio. Series Natural sciences/ Original reports 5/1984. 88 p. + original publications.

  19. KOLJONEN, M.-L. 1985. Ihmisen toiminnan vaikutus lohen perinnölliseen rakenteeseen (Human impact on genetic structure of the salmon). Helsinki. RKTL, kalantutkimusosasto. Monistettuja julkaisuja 18. 39 p.

  20. KOLJONEN, M. -L. 1985. Suomen lohikantojen entsyymigeneettinen muuntelu (Enzyme gene variation in Finnish salmon stocks). Helsinki. RKTL, kalantutkimusosasto. Monistettuja julkaisuja 37. 94 p.

  21. LAHTI, E. 1985. On the thyroid function of cold-water fish, especially vendace (Coregonus albula L.), in fresh and brackish water. Publications of the University of Kuopio, Series Natural sciences/Original reports 4/1985. 67 p.

  22. LAHTI, E., HARRI, M. & LINDQVIST, O.V. 1985. Uptake and distribution of radioiodine, and the effect of ambient nitrate, in some fish species. Comp. Biochem. Physiol. 80A(3), p. 337–342.

  23. LAHTI, E. & LINDQVIST. O.V. 1984. The iodine content of the tissues of vendace (Coregonus albula) in correlation to the iodine content of the ambient water. Aqua Fennica 14(2), p. 197–203.

  24. LEHTONEN, H., MIINA, T. & FRISK, T. 1984. Natural occurrence of pike-perch (Stizostedion lucioperca L.) and success of introduction in relation to water quality and lake area in Finland. Aqua Fennica 14(2), p. 189–196.

  25. LINDSTRÖM-SEPPÄ, P. 1985. Seasonal variation of the xenobiotic metabolizing enzyme activities in the liver of male and female vendace (Coregonus albula L.). Aquatic Toxicology 6, p. 323–331.

  26. LINDSTRÖM-SEPPÄ, P., KOIVUSAARI, U., HÄNNINEN, O. & PYYSALO, H. 1985. Cytochrome P-450 and monooxygenase activities in the biomonitoring of aquatic environment. Pharmazie 40(4), p. 232–234.

  27. LODENIUS, M. 1985. The mercury problem and fishing in Finland. In: Economics of ecosystem management. Eds. D.O. Hall, N. Myers & N.S. Margaris. Dordrecht. p. 99–103.

  28. MILLS, C.A. & ELORANTA, A. 1985. Reproductive strategies in the stone loach Noemachilus barbatulus. Oikos 44, p. 341–349.

  29. MILLS, C.A. & ELORANTA, A. 1985. The biology of Phoxinus phoxinus (L.) and other littoral zone fishes in Lake Konnevesi, Central Finland. Ann. Zool. Fennici 22, p. 1–12.

  30. MYLLYLÄ, M., TORSSONEN, M., PULLIAINEN, E. & KUUSELA, K. 1984. Biological studies on the minnow, Phoxinus phoxinus, in Northern Finland. Aquilo, Ser. Zool. 22, p. 149–156.

  31. NIEMI, M. 1985. Fecal indicator bacteria at freshwater rainbow trout (Salmo gairdneri) farms. Helsinki. Publications of the Water Research Institute 64. 49 p.

  32. NIKINMAA, M., JÄRVENPÄÄ, T., WESTMAN, K. & SOIVIO, A. 1985. Effects of hypoxia and acidification on the haemolymph pH values and ion concentrations in the freshwater crayfish (Astacus astacus L.). Finnish Fish. Res. 5, p. 17–22.

  33. OIKARI, A., NIKINMAA, M., LINDGREN, S. & LÖNN, B.-E. 1985. Subiethal effects of simulated pulp mill effluents on the respiration and energy metabolism of rainbow trout (Salmo gairdneri). Ecotoxicol. Environm. Safety 9, p. 378–384.

  34. OIKARI, A., SOIVIO, A., VUORINEN, M., VUORINEN, P.J. & NYHOLM, K. 1985. Metsäteollisuuden jätevesistä ja jätevesikomponenteista sekä niiden vaikutuksista kaloihin (On waste effluents from the forest industry, their composition and their effects on the fishes). Helsinki. RKTL, kalantutkimusosasto. Monistettuja julkaisuja 23, p. 119–192.

  35. OIKARI, A. & VIRTANEN, E. 1984. Influence of temperature acclimation on renal hydromineral metabolism in smolts of Salmo salar. J. Therm. Biol. 9(3), 215–220.

  36. PARTANEN, H. 1985. Suurtaloudet kalanmarkkinointijärjestelmässä (Large scale consumers and the fish markets). Helsinki. RKTL, kalantutkimusosasto. Monistettuja julkaisuja 26, p. 95–151.

  37. PERSSON, P.-E. 1985. Kalojen aistinvarainen arviointi. Suositukset kalojen haju- ja makuvirheiden tutkimiseksi (Organoleptic evaluation of fish. Recommended checks for off-flavours). Helsinki. RKTL, kalantutkimusosasto. Monistettuja julkaisuja 33, p. 189–206.

  38. PRUUKI, V., ANTTINEN, P. & AHVONEN, A. 1985. Tornion- ja Muonionjoen vesistön kalataloustutkimus (Study on the fisheries of the Tornionjoki and Muonionjoki river systems). Helsinki. RKTL, kalantutkimusosasto. Monistettuja julkaisuja 32. 227 p.

  39. PURSIAINEN, M., ASLA, I., KANNEL, R. & WESTMAN, K. 1985. Lohenpoikasten vapautusallaskokeet Selkämeren rannikolla vuosina 1983–1984 (Experiments on releasing ponds for salmon on the coast of the southern part of the Gulf of Bothnia). Helsinki. RKTL, kalantutkimusosasto. Monistettuja julkaisuja 42, p. 29–62.

  40. PURSIAINEN, M., JÄRVENPÄÄ, T., WESTMAN, K., TIKKA, J., KUITTINEN, E. & LOUHIMO, J. 1984. Kyrönjoen vesistöalueen rapukantojen tila ja nykyiset ravuntuotantoedellytykset (Condition of crayfish stocks in the Kyrönjoki River). Helsinki. Vesihallitus, tiedotus 247 A, p. 33–64.

  41. PURSIAINEN, M. & TULONEN, J. 1985. Eel escapement from small forest lakes. Vie et Millieu. (in press)

  42. PÄRJÄLÄ, E., TAMMINEN, A. & LINDQVIST, O.V. 1984. Pollution loadings from Finnish inland fish-farms: a case study. Aqua Fennica 14(2), p. 205–214.

  43. RAHKONEN, R., VALTONEN, E.T. & GIBSON, D.I. 1984. Trematodes in Northern Finland II: The occurrence of Bunodera luciopercae (Müller 1776) in three different kind of water bodies. Bothnian Bay Rep. 3, p. 55–65.

  44. RAILO, E., NIKINMAA, M. & SOIVIO, A. 1985. Effects of sampling on blood parameters in the rainbow trout, Salmo gairdneri Richardson. J. Fish. Biol. 26, p. 725–732.

  45. RANTA, E. & NUUTINEN, V. 1984. Zooplankton predation by rockpool fish (Tinca tinca L. and Pungitius pungitius L.): an experimental study. Ann. Zool. Fennici 21, p. 441–449.

  46. RASK, M. 1984. The effect of low pH on perch, Perca fluviatilis L. II. The effect of acid stress on different development stages of perch. Ann. Zool. Fennici 21, p. 9–13.

  47. RASK, M. 1984. The effect of low pH on perch, Perca fluviatilis L. III. The perch population in a small, acidic, extremely humic forest lake. Ann. Zool. Fennici 21, p. 15–22.

  48. RASK, M. & ARVOLA. L. 1985. The biomass and production of pike, perch and whitefish in two small lakes in southern Finland. Ann. Zool. Fennici 22, p. 129–136.

  49. RASK, M. & HIISIVUORI, C. 1985. The predation on Asellus aquaticus (L.) by perch, Perca fluviatilis (L.), in a small forest lake. Hydrobiol. 121, p. 27–33.

  50. RINTAMÄKI, P., VALTONEN, T. & FREDRICHS, G.N. 1985. Occurrence of Yersinia ruckeri infection in farmed whitefish and Atlantic salmon in Northern Finland. J. Fish. Dis. (in press).

  51. Saimaan ekologinen tutkimus vuosina 1980–1983 (Ecological study of Lake Saimaa in the years 1980–1983). Ed. L. Hakkari. Helsinki 1985. Vesihallitus, tiedotus 255. 380 p.

  52. SALOJÄRVI, K., PARTANEN, H., AUVINEN, H., JURVELIUS, J., JÄNTTI-HUHTANEN, N. & RAJAKALLIO, R. 1985. Oulujärven kalata-louden kehittämissuunnitelma. Osa I: Nykytila (Plan for the development of the fishery of Lake Oulujärvi. Part I: Present condition). Helsinki. RKTL, kalantutkimusosasto. Monistettuja julkaisuja 40. 278 p.

  53. SALOJÄRVI, K. & PARTANEN, H. 1985. Oulujärven kalatalouden kehittämissuunnitelma. Osa II: Suunnitelma (Plan for the development of the fishery of Lake Oulujärvi. Part II: Plan). Helsinki. RKTL, kalantutkimusosasto. Monistettuja julkaisuja 41. 116 p.

  54. SOIVIO, A. & VIRTANEN, E. 1985. The quality and condition of reared Salmo salar smolts in relation to their adult recapture rate. Aquaculture 45, p. 335–343.

  55. SUMARI, O., SIITONEN, L. & LINDER, D. 1985. Valtakunnallinen kirjolohen rodunjalostusohjelma (National plan for improving the races of rainbow trout). Helsinki. RKTL, kalantutkimusosasto. Monistettuja julkaisuja 30. 82 p.

  56. TANA, J. & NIKUNEN, E. 1985. Impact of pulp and paper mill effluent on egg hatchability of pike (Esox lucius). Bull. Environm. Cont. Toxicol. (in press)

  57. TUUNAINEN, P., NYLANDER, A., ALAPASSI, T. & AIKIO, V. 1985. Kalastus ja kalakannat Tornionjoen vesistössä (Fishing and fish stocks in the Tornionjoki river system). Helsinki. RKTL, kalantutkimusosasto. Monistettuja julkaisuja 25. 86 p.

  58. TUURALA, H., NIKINMAA, M. & SOIVIO, A. 1985. Gill damage as a determinant of residual oxygen concentration in the sealed jar test. Bull. Environm. Cont. Toxicol. 34, p. 385–389.

  59. Vaelluskalakantojen elvyttämistyöryhmän muistio (Memorandum of the working group for the rehabilitation of migratory fish stocks). Helsinki. Maa- ja metsätalousministeriö. Työryhmämuistio MMM 1985:7. 129 p.

  60. VALTONEN, E.T., GIBSON, D.I. & KURTTILA, M. 1984. Trematodes in Northern Finland I: Species maturing in fishes in the north-eastern Bothnian Bay and in a local lake. Bothnian Bay Rep. 3, 31–44.

  61. VERTA, M. 1984. The mercury cycle in lakes; some new hypotheses. Aqua Fennica 14(2), p. 215–221.

  62. VIITANEN, M., NIEMINEN, M. & ROSBERG, T. 1985. Ammattimaisesti kalastetun kalan käyttö teollisuudessa (Use of commercial fish catches in industry). Helsinki. RKTL, kalantutkimusosasto. Monistettuja julkaisuja 29. 90 p.

  63. VIRTANEN, E. & SOIVIO, A. 1984. Effects of low acclimation temperature on salinity adaptation in the presmolt salmon, Salmo salar L.. Comp. Biochem. Physiol. 78A(2), p. 387–392.

  64. VIRTANEN, E. & SOIVIO, A. 1985. The patterns of T4, T3 -cortisol and Na, K -ATPase during smoltification of hatchery reared Salmo salar and comparison with wild smolts. Aquaculture 45, p. 97–109.

  65. VUORINEN, P.J. & VUORINEN, M. 1985. Effects of bleached kraft mill effluent on reproduction of brown trout (Salmo trutta L.) on a restricted diet. Finnish Fish. Res. 6. (in press)

  66. VUORINEN, M. & VUORINEN, P.J. 1985. Sublethal effects of an organobromide slimecide on starving brown trout (Salmo trutta L.). Finnish Fish. Res. 5, p. 23–30.

  67. VUORINEN, P.J., VUORINEN, M. & NYHOLM, K. 1984. Vesistöihin joutuvien aineiden haitallisista vaikutuksista kaloihin ja vaikutusten tutkimusmenetelmistä (Effects of harmful subtances on the fishes of the receiving waters and methods of investigating these effects). Helsinki. RKTL, kalantutkimusosasto. Monistettuja julkaisuja 23, p. 35–118.

  68. VUORINEN, P.J., VUORINEN, M., NYHOLM, K., SOIVIO, A. & OIKARI, A. 1984. Fysiologisten menetelmien soveltaminen kalataloudellisten vahinkojen ja haittojen määrittämiseen (Application of physiological methods in the assessment of damage to fisheries). Helsinki. RKTL, kalantutkimusosasto. Monistettuja julkaisuja 23, p. 1–34.

  69. WESTMAN, K. & NYLUND, V. 1985. Rapu ja ravustus (Crayfish and crayfish fisheries). Helsinki, Weilin & Göös. 173 p.

  70. WESTMAN, K., PURSIANEN, M., NYLUND, V. & JÄRVENPÄÄ, T. 1985. Raputaloudelliset tarkkailu- ja vesistötutkimukset. Tavoitteet, menetelmä ja toteutus (Research on crayfish fisheries and waters. Aims, methods and realization). Helsinki. RKTL, kalantutkimusosasto. Monistettuja julkaisuja 33, p. 207–265.

  71. WESTMAN, K., SÄRKKÄ, J., PURSIAINEN, M. & SUMARI, O. 1985. Structure and food of crayfish Astacus astacus populations in two Finnish rivers. In: Freshwater crayfish 6. Ed P. Brinck. Lund. (in press)

APPENDIX 1

FISHING IN 1984,     Catch 1 000 kg

      SEA FISHERIES     FRESHWATER FISHERIES     TOTAL
Professional fishermenSemiprofessional fishermanNon-professional fishermanTotalProfessional fishermenSemiprofessional fishermanNon-professional fishermanTotalProfessional fishermenSemiprofessional fishermanNon-professional fishermanTotal
Fishermen1 8932 842143 503148 2382982 161538 621541 0802 1915 003682 124689 318
Baltic herring89 3647 0351 00997 408----89 3647 0351 00997 408
Sprat2 3872472 436----2 3872472 436
Cod6 9109511 6999 560----6 9109511 6999 560
Flounder7134285390----7134285390
Atlantic salmon1 039115661 2205846591 0441231121 279
Brown trout95501803253134044209863584745
Whitefish7915908032 1841531561 2811 5909447462 0813 774
Vendace10465432121 7232 0932 1345 9501 8272 1582 1776 162
Smelt405199316351910774200424306105835
Common bream23025836285017431 5921 6522473011 9542 502
Ide1631851321451511703036236302
Pike2022751 1721 6491301915 7276 0483324666 8997 697
Roach16686727979681323 4623 6622342184 1894 641
Perch2932131 7052 21149967 6837 8283423099 38810 039
Pike-perch21980217516549242296224129459812
Burbot11912223547699991 0311 2292182211 2661 705
Eel1089012829113638
Others231699339333585706612641276631 054
Total102 64310 1758 767121 5852 3183 05124 42529 794104 96113 22633 192151 379

APPENDIX 2

KALANVILJELY VUONNA 1984 — FISKODLING ÅR 1984 — FISH CULTURE IN 1984

KALANVILJELYLAITOSTEN LUKUMÄÄRÄMerilaitoksetSisävesilaitoksetLuonnonravintolam-mikkoyrityksetYhteensä
ANTAL FISKODLINGS-ANSTALTERAnläggningar i havetAnläggningar i sött vattenNaturdammsföretagInalles
NUMBER OF FISH FARMS AND HATCHERIESBrackish water cage farmsFresh water farms and hatcheriesNatural rearing pond breedersTotal
 151302222
675


KALANVILJELYLAITOS-TEN TUOTANTOTILAT

FISKODLINGSANSTALTERNAS PRODUKTIONSUTRYMME

PRODUCTION CAPACITY OF FARMS AND HATCHERIES
Haudontakapasiteetti
Kläckningskapacitet
Incubation capacity
Kasvatustilat
Uppfödningsutrymme
Rearing space
     Verkkoaltaita ja-aitauksia
Nätkassar ochinhägnader
Net cages and enclosures
 
Suppilohaudonta
Kläckning i glas
Glass incubation
Asettihaudonta
Backkläckning
Tray incubation
Keinoaltaita
Konstgjorda bassänger
Artificial tanks
Maa-altaita
Jorddammar
Eart ponds
Merialue
Havsområde
Sea area
Sisävesialue
Sötvattensområde
Freswater area
Luonnonravintolammikoita
Naturnäringsdammar
Natural food rearing ponds
Mätilitraa
Liter rom
Egg liters
      
    kpl 3518 1807 1303 154 780
  1000 m2    
  16050      17759 40   958   427  119   ha8499
Laitoksia - Anstalter -
Farms and hatcheries
    596583  228  151  24222


KALANVILJELYLAITOSTEN1) RUOKAKALATUOTANTOMerilaitoksetSisävesilaitoksetYhteensäTuotannon arvo Mmk
FISKODLINGSANSTALTERNAS MATFISKPRODUKTIONAnläggningar i havetAnläggningar i sött vattenInallesProduktionens värde M Fmk
FOOD FISH PRODUCTION OF FISH FARMSBrackish water cage farmsFresh water farmsTotalValue of production M Fmk
 Tuotanto - Produktion - Production 1000 kg2) 
     5381    4112    9493    204.0
Laitoksia - Anstalter - Farms        151        184        335 

1) Tuotannosta kirjolohta 99 %. Jäännös lohta ja taimenta. - Av produktionen 99% regnbågslax.
Resten lax och öring. - 99 % of production rainbow trout. The rest salmon and brown trout.

2) Tuotantoluvut perkaamatonta painoa. - Produktionssiffrorna som orensad fisk. Production in kg ungutted fish.


ISTUTUKSIIN KÄYTETTY TUOTANTO 1984
PRODUCTION FÖR UTSÄTTNING 1984
PRODUCTION TO STOCKINGS 1984
Vastakuoriutuneet nykläckta newly hatched 3)1-kesäiset
l-somriga
1-summer old 4)
1-vuotiaat
1-åriga
1 year old
2-kesäiset
2-somriga
2 summers old
2-vuotiaat
2-åriga
2 years old
3-kesäiset
3-somriga
3 summers old
3-vuotiaat
3-åriga
3 years old
vanhemma
äldre
older
Yhteensä (ei sisällä vastakuoriutuneita)
Inalles (nykläckta inte med)
Total (excl. newly hatched)
Istutukset 1000 kpl - Utsättningar 1000 st - Stockings 1000 fish
Pohjasiika - Sik - Whitefish Coregonus pidschian (Gmelin)
3188
2139
6
20
-
-
-
-
2165
Vaellussiika - Sik - Whitefish Coregonus lavaretus (L.) s.str.
86735
7895
-
1124
-
-
-
-
9019
Planktonsiika - Sik - Whitefish Coregonus muksun (Pallas)
10435
21447
-
68
-
13
-
0
21528
Peledsiika - Sik - Whitefish Coregonus peled (Gmelin) s. Berg
21195
1934
-
-
-
1
-
-
1935
Siika, laji tuntem.- Sik, art okänd Whitefish, unidentif.- Coregonus sp.
38
126
20
-
-
-
-
-
146
Muikku - Siklöja - Vendace Coregonus albula (L.)
1475
-
-
-
-
-
-
-
-
Lohi - Lax - Atlantic salmon Salmo salar L.
1566
123
421
18
1606
-
27
1
2196
Järvilohi - Insjölax - Landlocked salmon Salmo salar m. sebago Girard
-
22
-
-
27
1
20
-
70
Meritaimen - Havsöring - Sea trout Salmo trutta m. trutta L.
1524
424
81
248
727
64
-
3
1547
Järvitaimen - Insjö-öring - Brown trout Salmo trutta m. lacustris L.
3580
252
361
177
764
25
151
16
1746
Purotaimen - Bäcköring - Brown trout non-migratory - Salmo trutta m. fario L.
860
5
5
17
43
-
-
-
70
Kirjolohi - Regnbågsforell - Rainbow trout Salmo gairdneri Richardson
-
63
288
2
5
-
0
-
358
Nieriä - Röding - Char Salvelinus alpinus (L.)
805
69
-
4
22
4
22
-
121
Puronieriä - Bäckröding - Brook trout Salvelinus fontinalis (Mitchill)
-
20
-
-
1
-
-
-
21
Harmaanieriä - Kanadaröding - Lake trout Salvelinus namaycush (Walbaum)
100
-
-
47
71
-
-
-
118
Harjus - Harr - Crayling Thymallus thymallus (L.)
525
572
6
3
-
-
-
-
581
Hauki - Gädda - Pike Esox lucius L.
13100
1572
-
-
-
-
-
-
1572
Lahna - Braxen - Bream Abramis brama (L.)
-
220
-
-
-
-
-
10
230
Karppi - Karp - Carp Cyprinus carpio L.
-
-
-
6
1
1
-
-
8
Säyne - Id - Id Leuciscus idus (L.)
-
104
-
-
-
-
-
-
104
Kuha - Gös - Pike-perch Stizostedion lucioperca (L.)
112
1447
-
-
-
-
-
-
1447
Rapu - Flodkräfta - Crayfish Astacus astacus L.
-
1
-
-
-
-
-
-
1
Täplärapu - Signalkräfta - American crayfish Pacifastacus leniusculus (Dana)
-
3
-
-
-
-
-
-
3

3) Lohi-, taimen- ja nieriälajien osalta syömäänoppineita, vapaasti uivia poikasia. - Beträffande lax, öring och röding, yngel som börjat äta och simmar fritt.- Salmonids free-swimming fries.

4) Hauen osalta esikesäisiä, muutaman viikon ikäisiä poikasia. - Beträffande gäddan nykläckta, några veckor gamla yngel. - Pikes a few veeks weeks old younglings.

Istutustuotannon arvo 1984 M mk 65,0
Utsättningsproduktionens värde 1984 M Fmk 65,0
Value of stocking-production 1984 M Fmk 65,0


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