ПАРАЗИТОЛОГИЯ, 51, 5, 2017

УДК 576.89:597.552.3

THE PARASITE FAUNA OF ECOLOGICAL FORMS OF THE EUROPEAN , EPERLANUS L.

© L. V. Anikieva,1 E. P. Ieshko,2 O. N. Pugachev3

12 Institute of Biology, Karelian Research Centre RAS 11 Pushkinskaya St., 185910 Petrozavodsk, Republic of Karelia 3 Zoological Institute RAS 1 Universitetskaya Nab., 199034 St Petersburg 1 E-mail: [email protected] Submitted 19.05.2017

Three ecological forms of smelt have been analyzed: an anadromous (marine) form from the North Sea drainage basin and two freshwater forms — smelt proper from lakes Ladoga, Onego and Pyaozero, and dwarf (lake) smelt from lakes Beloye, Vozhe and Peipus (Pskov-Chudskoye). It is demonstrated that ecological forms of smelt feature their specific sets of parasites and the taxonomic structure of their diversity as represented by the compo- sition of higher taxa. It is shown that ecological forms of smelt are characterized by a speci- fic set of parasites and systematic structure of its diversity, which is assessed on the compo- sition of the higher taxa. Most significant differences were detected between the anadromo- us form inhabiting waters of varying salinity and the freshwater form. These characteristics of the parasite fauna stem from smelt's high ecological plasticity, which enables the to inhabit both marine and fresh waters. Key words: smelt Osmerus eperlanus, ecological forms, parasite composition, diversity structure.

ПАРАЗИТОФАУНА ЭКОЛОГИЧЕСКИХ ФОРМ ЕВРОПЕЙСКОЙ КОРЮШКИ OSMERUS EPERLANUS L.

© Л. В. Аникиева,1 Е. П. Иешко,2 О. Н. Пугачев3

12 Институт биологии Карельского научного центра РАН ул. Пушкинская, 11, Петрозаводск, Республика Карелия, 185910 3 Зоологический институт РАН Университетская наб., 1, Санкт-Петербург, 199034 1 [email protected] Поступила 19.05.2017

Проведен анализ паразитофауны трех экологических форм европейской корюш- ки: проходной (морской) из бассейна Северного моря и двух пресноводных форм — собственно корюшки из озер Ладожское, Онежское и Пяозеро и снетка из озер Белое,

369 Воже и Псковско-Чудское. Показано, что экологические формы корюшки характери- зуются специфичным набором паразитов и систематической структурой его разнооб- разия, которое оценивается по составу высших таксонов. Максимальные различия выявлены между проходной, обитающей в водоемах с разным градиентом солености, и пресноводной формами корюшек. Эти особенности паразитофауны являются ре- зультатом большой экологической пластичности корюшки, которая позволяет ей обитать в морских и пресноводных водоемах. Ключевые слова: корюшка Osmerus eperlanus, экологические формы, видовой со- став паразитов, структура разнообразия.

The European smelt has a wide North European range from France (the Loi- re) to the Baltic, White and Barents Seas, including the south-eastern part of the Scandinavian Peninsula and southwestern Ireland. The Russian range spans the catchments of all of these seas. The species occurs in the Kola Peninsula, is wi- despread in Karelia, and waterbodies from the Northern Dvina to the Pechora ri- vers and lakes of Bolshezemelskaya tundra (..., 2010). Smelt have disper- sed widely across Northern Europe after the last deglaciation and adapted to a variety of ecological conditions, having differentiated into anadromous, lacust- rine-riverine, and lacustrine forms. Anadromous smelt are quite widespread in the drainage basins of the Baltic and the North Seas, as well as along North At- lantic coasts. They spend most of their lives in marine coastal waters, ascending rivers to spawn. The freshwater form comprises 2 groups: smelt proper (lacust- rine-riverine) — large-sized form passing from a planktonic diet to predation during the life cycle, and dwarf (lake) smelt — small-sized precocious fish that remain planktivorous throughout their life (Petrov, 1940; Berg, 1948; Klyuka- nov, 1977; Atlas..., 2003; Fishes..., 2010). The origins of the ecological forms of the European smelt have been poorly investigated. The composition and structu- re of the species have been discussed and revised for decades (Atlas..., 2003; Sendek et al., 2005; Kovpak et al., 2010; Skurikhina et al., 2010; Kottelat and Freyhof 2007, etc.). A key reason for studying the parasite fauna of smelt is to assess the specific characteristics of its life and habitat conditions in various waterbodies. Trophic connections between the hosts of parasites with a complex life cycle create the background for using them as indicators of fish nutrition. The aim of this study was to analyze and compare the parasite fauna in diffe- rent ecological forms of smelt to assess the species' structure and distinctions between the ecological forms.

MATERIALS AND METHODS

The paper is based on the authors' own materials and published data on smelt parasites. We analyzed the species composition of parasites in smelt from waters of Karelia (lakes Ladoga, Onego, Pyaozero), Vologda and Pskov Regi- ons (lakes Beloye, Vozhe, Peipus), and the North Sea drainage basin. Lakes La- doga, Onego, and Pyaozero are inhabited by the lacustrine-riverine form of smelt, lakes Beloye, Vozhe, Peipus by dwarf smelt, the North Sea basin by ana- dromous smelt (Berg, 1948; Smirnova-Stefanovskaya, 1967; Ivanova, 1982; At- las..., 2003).

370 The similarity of the species composition of smelt parasites was estimated by the principal component analysis method (Korosov, Gorbach, 2010). In additi- on, archival materials from the Laboratory of and Plant Parasitology at the Institute of Biology, Karelian Research Centre RAS were used.

RESULTS

The parasite fauna of anadromous smelt from the North Sea drainage basin comprises 29 species (Kahl, 1936; Voigt, 1975; Jarling, 1982; Möller and Klatt, 1990; Obickezie et al., 1992; Anders and Wiese, 1993; Palm et al., 1999; Kuhn et al., 2013). Ten species belong to the freshwater ecological group. This group is heterogeneous, represented by parasites differing in host specificity. Three species mainly occur in smelts — protozoa Pleistophora ladogensis Voronin, 1978 and Eimeria osmeri Molnar, Fernando, 1974, as well as the cestode Prote- ocephalus tetrastomus (Rudolphi, 1810); 2 species predominantly parasitize sal- monoids — the cestode Diphyllobothrium ditremum (Creplin, 1825), and the Cystidicola farionis Fischer, 1798; and 6 species are wide genera- lists — metacercariae of the genus Diplostomum Nordman, 1832, nematode Cammalanus truncatus (Rudolphi, 1814), crustacean Ergasilus sieboldi Nord- mann, 1832, leech Piscicola geometra Linnaeus, 1761, glochidium Anodonta anatina L., 1758. Nineteen species belong to the marine ecological group. They are widespread parasites with a complex life cycle. The number of species is the highest for . The list of parasites for the North Sea drainage basin inc- ludes all species of marine nematodes and acanthocephalans known from smelt in its entire species range (Anikieva and Ieshko, 2017). The number of species in the parasite fauna of lacustrine-riverine smelt inha- biting lakes of Karelia is similar to that of anadromous smelt from the North Sea basin. The greatest number of species (29) was found in smelt from Lake Lado- ga (Rumyantsev et al., 1979, 1984, 2001; Rumyantsev, Permyakov, 1994; Ru- myantsev, Ieshko, 1997; Anikieva, 1998; Rumyantsev, 2007). Differences bet- ween parasite faunas of anadromous and lacustrine-riverine smelts consist in the ratio of ecological groups of parasites and the number of species within these groups. Lacustrine-riverine smelt host only 2 marine species — relict acantho- cephalans of the genus Corynosoma Lühe, 1904, whose definitive host include the ringed seal Pusa hispida (Schreber, 1775) — a marine relict and endemic species of Lake Ladoga. All other parasites in lacustrine-riverine smelt belong to the freshwater ecological group. Smelt in Onego and Ladoga Lakes have similar species compositions of pa- rasites typical of the freshwater ecological group. Smelt from these lakes had the highest number of freshwater parasite species. This group included all speci- fic parasites of smelts — protozoans Eimeria osmeri Molnar, Fernando, 1974, Pleistophora ladogensis, and Glugea hertwigi Weissenberg, 1921, the monoge- nean Gyrodactylus osmeri Rumyantsev, Schulman, Iyeshko, 1998, and the ces- tode Proteocephalus tetrastomus. A substantial component of the parasite fauna are species whose development involves zooplankton, spezialist smelt parasite Proteocephalus tetrastomus, salmonoid parasites P. longicollis, Diphyllobo- thrium ditremum, Eubothrium salvelini Schrank, 1790. A few plerocercoids of the broad tapeworm Diphyllobothrium latum (Linnaeus, 1758) have been found.

371 There is a wide representation of parasites developing through a stage involving zoobenthos. These are trematodes of the genus Diplostomum, Ichtyocotylurus erraticus (Rudolphi, 1809) Odening, 1969, and the nematode Raphidascaris acus (Bloch, 1779) — broad generalists. The life cycles of Echinorhynchus sal- monis Mueller, 1780, Cystidicola farionis, Corynosoma are linked with relict crustaceans. The smelt parasite fauna from Lake Pyaozero differs from that of Ladoga and Onego Lakes in a smaller total number of species, fewer species in certain taxonomic groups, and absence of crustaceans. It does however com- prise a majority of parasite species typical in lacustrine-riverine smelt. The parasite fauna of the dwarf smelt comprises fewer species being compa- red to lacustrine-riverine and anadromous forms (Kogteva, 1957; Izyumova, 1974; Radchenko, 1999, 2002). Protozoa within it are few. The dwarf smelt from Lake Beloye hosted only two species of protozoans, a specialist parasite Glugea hertwigi at a low prevalence (1.7 %) and generalist infusorians of the genus Capriniana Mazzarelli, 1906 (not identified to species). Dermocystidium sp. was found in the dwarf smelt from Lake Beloye — 6.6 % (Radchenko, 1999). In this lake, Radchenko (1999) also retrieved Dermocystidium from perch and pike, and identified it as D. percae Reichenbach-Klinke, 1950. The rest of parasites have a complex life cycle and either occur in a wide range of fish hosts or specialize in another taxonomic group of hosts. Of the 16 parasite species found in the dwarf smelt from Lake Beloye, five species were parasites of salmonoid fish — Eubothrium crassum (Bloch, 1779), Diphyllobothrium dit- remum, Proteocephalus longicollis, Phyllodistomum umblae (Fabricius, 1780) Bake, 1982, and Ichthyocotylurus erraticus, 3 species had cyprinids and 2 speci- es had percids as their preferred hosts, and the rest were broad generalists. The parasite fauna of the dwarf smelt from Lake Vozhe includes species with a complex life cycle — parasites of salmonoid, percid and cyprinid fish. Among the total 8 parasite species, there were 2 species of cestodes (Proteoce- phalus longicollis, Triaenophorus crassus Forel, 1868), 3 trematodes (Diplosto- mum baeri, Ichthyocotylurus variegatus (Creplin, 1825), and I. erraticus), and 3 nematodes (Cystidicola farionis, Camallanus lacustris (Zoega, 1776), and Raphidascaris acus). There were no specialist parasites. Two cestode spe- cies (T. crassus, and Eubothrium crassum) found in dwarf smelts from lakes Vozhe, and Beloye (Radchenko, 1999, 2002) were atypical for freshwater eco- forms of the smelt. Two T. crassus plerocercoids were isolated from muscles of two 0 + dwarf smelt from Lake Vozhe in autumn (Radchenko, 2002, p. 25). T. crassus was found in Lake Ladoga in smelt of the lacustrine-riverine form — 7 % (Baryscheva and Bauer, 1957; Rumyantsev, 2007). Rybak (1982) postula- ted that finding of T. crassus in smelt from Lake Segozero was the result of the parasite's invasion in the smelt stocked into the lake as eggs from Lake Ladoga. There are several reasons to doubt findings of E. crassum in dwarf smelt from Lake Beloye. For this lake, E. crassum has been reported also from pike-perch, Sander volgensis (Gmelin, 1788) — a species of the family Perci- dae. Identification of larval stages of the genus Eubothrium cestodes to species is complicated by the lack of reliable discriminating traits. The life cycle of E. crassum can occur as two alternative patterns. The first one involves two in- termediate hosts (the first intermediate host is represented by copepods, the se- cond one, by the vendace). The second pattern includes a single intermediate host. In the latter case, the parasite's plerocercoid and adult stages are combined

372 Ordination onto the axes on the principal components of differences in the parasite fauna of smelt from. 1 — North Sea drainage basin, 2 — Lake Ladoga, 3 — Lake Onego, 4 — Lake Pyaozero, 5 — Lake Vozhe, 6 — Lake Peipus, 7 — Lake Beloye. within a single host species (vendace) (Kuperman, 1979; Anikieva et al., 2016). Since the only suitable definitive host for E. crassum in Lake Beloye is vendace, and the parasite has not been detected in this fish species, plerocercoids of the genus Eubothrium found in dwarf smelt and Volga pike-perch from this lake should rather be reported as parasites not identified to species level. The parasite fauna of dwarf smelt in Lake Peipus comprises 7 species: sal- monoid parasites Ichthyocotylurus erraticus, Proteocephalus longicollis, and Diphyllobothrium ditremum, predominantly percid parasites Triaenophorus no- dulosus (Pallas, 1781), Camallanus lacustris, a cyprinid parasite Bucephalus polymorphus Baer, 1827, and a broad generalist Ergasilus sieboldi. Noteworthy is the absence in Lake Peipus of a parasite causing epizootic events in dwarf smelt, the myxosporidian Glugea hertwigi, which has been reported from lakes Seliger, Ilmen and Pestovo (Kogteva, 1957). Principal component analysis was employed to estimate the differentiation of the ecological forms of smelt by species composition of its parasites (see fi- gure). The analysis was performed on 59 parasite species retrieved from smelt from the waters in question. Factor loadings for component 1 are represented by a set often parasite species associated with salmonoid fish — Pseudocapillaria salvelini, Eubothrium salvelini, Echinorhynchus borealis, E. salmonis, broad generalists — Capriniana piscium, Trichodina pediculus, Tripartiella copiosa, Tylodelphys clavata, and 2 specialist parasites of smelt Eimeria osmeri and Gyrodactylus osmeri (Anikieva and Ieshko, in press). This set of species is res- ponsible for the distinctness of waterbodies harboring the lacustrine-riverine form of smelt: lakes Ladoga, Onego and Pyaozero. Factor loadings for compo- nent 2 are generated by 5 parasite species, including Corynosoma strumosum, C. semerme, Proteocephalus tetrastomus, which survived in fresh water as a re- licts, Pleistophora ladogensis — a parasite found also in the burbot in addition to the smelt, and a generalist Diplostomum spathaceum. In the coordinates of two principal components which explain 71 % of varia- tion of the parasite species diversity the investigated smelt populations form three discrete clusters (see figure). One of the clusters is represented by lacustri- ne-riverine forms of smelt from lakes Onego, Ladoga and Pyaozero. The lowest difference in the parasite fauna was observed between smelt from Lake Onego

373 and Lake Pyaozero, whose genesis was higher that of periglacial lakes. The pre- sence of endemic acanthocephalans of the genus Corynosoma in the parasite fa- una of fish from Ladoga created some distinction from lakes Onego and Pyao- zero. The second cluster comprises dwarf smelt from lakes Vozhe, Peipus and Be- loye. This form of smelt hosts few protozoa and specialist parasites. In this clus- ter, helminth species with a complex life cycle dominate. Differences between smelt from lakes Vozhe and Peipus in the composition of parasites were minor. The only somewhat isolated member in this cluster was the dwarf smelt from Lake Beloye. The third cluster is represented by the anadromous form of smelt from coas- tal waters of the North Sea, and a major share in the parasite fauna belongs to marine species. Anadromous smelt is the furthest from both freshwater forms in terms of the species composition of parasites and their taxonomic diversity.

DISCUSSION

Numerous observations of the life style and population structure of the Euro- pean smelt have revealed the species' outstandingly wide-ranging ecological variability and plasticity. Within its distribution range, smelt are represented by populations differing in abundance patterns, maturation time, spawning charac- teristics, dietary range and other parameters. In almost «every body of water smelt has a peculiar form shaped by the specific conditions in this waterbody» (Ivanova, 1982; p. 12). The properties of freshwater forms of smelt are not here- ditary. When environmental conditions change, «dwarf smelt» populations can acquire the traits typical of «smelt proper» populations, and vice versa (Kriksu- nov, Shatunovsky, 1979). The ability to modify biological characters to adapt to habitat conditions was demonstrated the most vividly when dwarf smelt was int- roduced in Volga reservoirs and when eggs of large-sized smelt from the Olon- ka River were stocked in Segozerskoye reservoir with the following dispersal to Lake Vygozero (Volodin, Ivanova, 1973; Ivanova, 1982). Studies of the genetic diversity and population structure of European smelt by allozyme electrophoresis and mitochondrial DNA restriction fragment length polymorphism (RFLP), analysis of variation in nucleotide sequences in mitoc- hondrial and nuclear DNA revealed a high genetic diversity and a poor populati- on genetic structuring (Gordeeva et al., 2005, 2009; Kovpak, 2010). In spite of the poor genetic differentiation, statistically significant differences between po- pulations were observed in allele frequencies at some polymorphic loci. For ins- tance, populations of anadromous smelt from the , lacustrine smelt from Lake Ladoga and dwarf smelt from Lake Beloye reliably differed on two out of four polymorphic genes (GPI-2 and PGM). The percentage of poly- morphic loci was the lowest for dwarf smelt from Lake Beloye. This same po- pulation was the most distant from anadromous smelt from the Gulf of Finland and lacustrine smelt from Lake Ladoga in terms of both genetic distances and F index values, which indicate the degree of reproductive isolation of populations (Sendek et al., 2005). Analysis of the species composition of parasites confirmed the differentiati- on of European smelt into anadromous and freshwater ecotypes (Atlas..., 2003;

374 Sendek et al., 2005; Fishes..., 2010). It was demonstrated that various ecological forms possess their own specific sets of parasites. The greatest differences were found between anadromous smelt, inhabiting waters with a gradient of saliniti- es, and freshwater forms of smelt. Anadromous smelt live in high salinity wa- ters and enter brackish river channels for spawning. The assortment of its para- sites reflects the smelt's ability to live under a wide range of abiotic conditions and its broad dietary spectrum, the bulk of it made up of mysids, side-swim- mers, decapods, with a smaller contribution of insect larvae, mollusks, polycha- etes, and other benthic organisms. The freshwater form of smelt had adapted to living in fresh water. The diverse composition of its parasite fauna also points to quite a wide dietary spectrum. The predominant component of the diet, howe- ver, is represented by planktonic crustaceans: cladocerans, copepods, and my- sids. Common items in smelt's diet are Eudiaptomus, Limnosida, Limnocala- nus, Bosmina, Cyclops, and Mysis. A comparison of the species composition of zooplankton with the diet composition of smelt showed that the latter accurately modeled the abundance of zooplankton in a waterbody (Maltseva, 1983; Niko- laev, 1983). Differences in the parasite fauna between freshwater forms of smelt (lacust- rine-riverine vs. dwarf smelt) also originate from the specific features of their life in individual lakes. Lacustrine-riverine smelt live in cold and deep oligot- rophic waters, such as lakes Ladoga, Onego, Pyaozero, inhabited by diverse composition of aquatic organisms. The parasite fauna of lacustrine-riverine smelt resembles that of anadromous smelt in the number of species, but differs in the set of species and the taxonomic diversity of parasites. The diversity of the parasite fauna reflects the wide dietary spectrum of lacustrine-riverine smelt. Smelt in lakes Ladoga, Onego and Pyaozero belong to the same ecological group — a large-sized form, but differ in the size-age composition, rates of length and weight increment, dietary characteristics and other parameters. In cold- and deep-water oligotrophic lakes young smelt grow and develop slowly. Maturation takes place relatively late. The age structure of the smelt population is complex, with a maximum life span of 6—10 years. Ladoga smelt (at spaw- ning) is 100 to 252 mm long. The bulk of the catches is made up of 1+ to 3+ fish 110—180 mm long. Onego smelt are smaller. The length of mature individuals ranges from 90 to 160 mm (Ivanova, 1982). The average length of Pyaozero smelt is 120 mm, average weight is 12 g. According to Kudersky (Kudersky, 2005), smelt had arrived to the large North European lakes Ladoga and Onego from different sources: to Ladoga from the Baltic Ice Lake, to Onego from the Upper Volga system of ice lakes. The parasite fauna of smelt in these lakes has a similar composition of specialist and common species but differs in rare species. Dwarf smelt is a precocious small-sized form of smelt. Lake Beloye is a me- sotrophic, mesohumic waterbody. The fish fauna is that of a classic zan- der-smelt lake. Lake Vozhe is an extensive shallow-water mesotrophic lake of the 'bream type'. Lake Peipus is a highly eutrophied shallow-water lake. Dwarf smelt in these lakes are typical representatives of a small-sized form of smelt. They mature at 1—2 years of age, 3—7 cm length and 0.4—3.1 g weight, rarely live as long as 4 years of age, and have an average length of 6—10 cm and we- ight of up to 6 g. The dominant component of dwarf smelt's dietary spectrum are cladocerans, with more diversity in autumn, when the food bolus of the fish contains up to 78 % (by weight) of copepods (Radchenko, 1999, 2002). The pa-

375 rasite fauna of dwarf smelt in these lakes is rather poor and made up of broad generalists. Thus, the analysis of the parasite fauna of European smelt revealed differen- ces in the species composition and structure of the taxonomic diversity of para- sites among ecological forms. The distinctions found in the parasite fauna ref- lect smelt's adaptations to a wide variety of environmental conditions. High ecological plasticity enables smelt to inhabit waters on a gradient of salinities and trophic levels. Conditions in the waterbodies and the life patterns of smelt in them are the factors providing differences in the parasite fauna between the va- rious ecological forms of smelt.

ACKNOWLEDGEMENTS

The authors are grateful to Yu. S. Reshetnikov (Severtsov Institute of Ecolo- gy and Evolution RAS) for support and valuable advice. The research was funded from the federal budget through allocations to imp- lementation of state order (N 0221-2014-0030).

References

Anders K.,Wiese V. 1993. Glochidia of the freshwater mussel Anadonta anatine, affecting the anadromous European smelt (Osmerus eperlanus) from the Eider estuary Germany. Journal of Fish Biology. 42: 411—419. Anikieva L. V. 1998. Cestodes of the genus Proteocephalus (Cestoda: Proteocephalidea) from the European smelt Osmerus eperlanus. Parazitologiya. 32 (2): 134—140. [In Rus- sian]. Anikieva L. V., Ieshko E. P. 2017. An annotated species list of parasites found in Europe- an smelt (Osmerus eperlanus L.). Proceeding of research KRC RAS. 7: 73—92. DOI: 10.17076/bg 627. [In Russian]. Anikieva L. V., Ieshko E. P., Rumyantsev E. A. 2016. Ecological analisis of helmints in vendace and smelt from lake Onego. Proceeding of research KRC RAS. ECOLOGI- CAL STUDIES Series. (4): 37—47. [In Russian]. Atlas of Russian Freshwater Fishes. 2003. In Two Volumes. Vol. 1. Edited by Yu. S. Reshet- nikov. Second edition. M.: Nauka. 379 p. [In Russian]. Baryscheva A. F., Bauer O. N. 1957. Fish parasites in Lake Ladoga. Bulletin of the Insti- tute of Fresh-water Fisheries. Vol. XLII. Parasites and Diseases of Fishes. Editors: G. Petrushewsky. L. 175—226. [In Russian]. Berg L. S. 1948. Fishes of fresh waters of the USSR and adjacent countries. M.; L.: Izd-vo an SSSR. Part 1. 466 p. [In Russian]. Gordeeva N. V., Sterligova O. P., Sendek D. S. 2005. Genetic variation in the smelt population from Syamozero lake. Biological resources of the White Sea and inland wa- ters of the European North. IV (XXVII) International conference. Part 1. (Vologda, Rus- sia, 5—10 December). Vologda. VSPU. 108—109. [In Russian]. Gordeeva N. V., KholodO.N., Dvoryankin G. A., Sendek D.S., Sterligo- va O. P. 2009. On the origin of the Solovetsky vendace and smelt of Syamozero. Journal of Ichtiology. 49 (1): 28—36. [In Russian]. Fishes in the nature reserves of . 2010. Yu. S. Reshetnikov) (ed.). Freshwater fish. Publishing House: Association of Scientific Publications KMK. 628 p. [In Russian]. Ivanova M. N. 1982. Population variability of fresh-water smelt. Rybinsk. Publishing house of the Institute of Biology of Inland Waters. A. V. Monakov (ed.). 143 p. [In Russian]. Izyumova N. A. 1974. Parasite fauna of the Lake Beloe, Rybinsk and Uglich reservoirs. Ins- titute of Biology of Inside Water RAS. Proceeding of research Institute of Biology of

376 Inland Waters. Issue 28. Flora, fauna and microorganisms of the Volga. Rybinsk: Pub- lishing house of the Institute of Biology of Inland Waters. 286—289. [In Russian]. Jarling C. 1982. On the helminth fauna of the smelt (Osmerus eperlanus L.) in the Elbe estu- ary. Archiv für Hydrobiologie. Supplement. 61 (3): 377—395. Kahl W. 1936. Über den Befall des Stints mit Larven des Fadenwurmes Porrcaecum de- cipiens. Der Fischmarkt. 4 (7): 118—120. Kerstan S. L. 1992. Der Befall von Fischen aus dem Wattenmeer und dem Nordatlantik 1988—1990 mit Nematodenlarven und eine Bibliographie über parasitische Nematoden in Fischen und Seesäugern. Ph. D. thesis. Berichte aus dem Institut für meereskunde an der Christian—Albrechts-Universität Kiel. 219. 205 p. Klyukanov V. A. 1977. Origin, settlement and evolution of smelt (Osmeridae). Proceedings of the Zoological Institute. Fundamentals of classification and phylogeny of Salmonids. Leningrad: Zoological institute of the Academy of Sciences of the USSR. 13—27. [In Russian]. Kogteva E. P. 1957. Parasites of fishes of the Pskov-Chudskoye reservoir. Bulletin of the Institute of Fresh-Water Fisheries. Vol. XLII. Parasites and Diseases of Fishes. G. Pet- rushewsky (ed.). L. 243—269. [In Russian]. Korosov A. V., Gorbach V. V. 2010. Computer processing ofbiological data: methodical manual. Petrozavodsk: Publishing house PetrSU. 83 p. [In Russian]. Kottelat M., Freyhof J. 2007. Handbook of European Freshwater Fishes. Delemont. IUCN. 660 p. Kovpak N. E. 2010. Intraspecific variability and phylogenetic relations of smelt fish of Rus- sia. Author's abstract. Dis... Cand. Biol. Sciences. Vladivostok. 23 p. [In Russian]. Kriksunov E. A., Shatunovsky M.I. 1979. Some questions of the variability of the structure of the smelt population Osmerus eperlanus L. Journal of Ichthyology. 19 (1): 55—62. [In Russian]. Kudersky L. A. 2005. Ways of formation of fish fauna of Lake. Proceeding of rese- arch KRC RAS. Biogeography of Karelia. Petrozavodsk. Publishing house: KarRC RAS. Issue. 7: 147—163. [In Russian]. Kuhn Th., Benninghoff T., Horst K., Landry Th., Klimpel S. 2013. Sealworm Pseudoterranova decipiens s. s. infection of European smelt Osmerus eperlanus in Ger- man coastal waters: ecological implications. Diseases of aquatic organisms. 102: 217— 224. doi: 10.3354/dao02555. Kuperman B.I. 1979. Ecological analysis of fish cestodes in the water bodies of the Volga- Baltic system (Rybinsk, Reservoir, Beloe, Onega and Ladoga Lake). Proceeding of recearch IBW. Issue 38 (41). Physiology and parasitology of freshwater . L.: Nauka. 133—159. [In Russian]. Maltseva V. V. 1983. Feeding of the vendace and smelt in the northeastern part of the One- ga Lake. Proceeding of recearch GosNIORKh. Fishes of Onega Lake and their eco- nomic use. Issue 205. L.: Izd-vo GosNIORH of NPO Promrybvod. 79—91. [In Rus- sian]. M ö ller H., Klatt S. 1990. Smelt as host of the sealworm (Pseudoterranova decipiens) in the Elbe estuary. In: Bowen W. D. (ed.). Population biology of seaworm (Pseudoterranova decipiens) in relation to its intermediate and seal hosts. Canadian Bulletin of Fisheries and Aquatic Sciences. 222: 129—138. Nikolaev 1.1. 1983. Ecological heterogeneity of the zooplankton of the Onega Lake and its significance in the dynamics of the abundance of the main planktophages of this reser- voir — the vendace and the smelt. Proceeding ofrecearch GosNIORH. Issue 205. Fish of Onega Lake and their economic use. L.: Izd-vo GosNIORH of NPO «Promrybvod». 67—79. [In Russian]. Obickezie A. I., Lick R., Kerstan S., Möller H. 1992. Larval nematodes in stomach wall granulomas of smelt Osmerus eperlanus from the German North Sea coast. Diseases of Aquatic Organisms. 12: 177—183. Palm H. W., Klimpel S., Bucher Ch. 1999. Checklist of metazoan fish parasites of German coastal waters. Berichte aus dem Institut für meereskunde an der Christian-Alb- rechts-Universität Kiel. Nr. 307. 155 p. D24105 Kiel. Dusternbrooker Weg. 20.

377 Petrov V. V. 1940. Whitebait of the Pskov-Chudskoe reservoir. News of VNIORH. L.: Izd-vo VNIORH. 23 (2): 47—76. [In Russian]. Radchenko N. M. 1999. Fish parasites of the Beloe Lake. Publishing house of the Vologda Institute of Educational Development. Vologda. 170 p. [In Russian]. Radchenko N. M. 2002. Fish parasites of Lake Vozhe. Publishing house of the Vologda Ins- titute of Educational Development. Vologda. 200 p. [In Russian]. Rumyantsev E. A. 2007. Fish parasites in the lakes of the European North. Petrozavodsk: Publishing house PetrSU. 252 p. [In Russian]. Rumyantsev E. A., Ieshko E. P. 1997. Parasites of fishes of reservoirs of Karelia. A sys- tematic catalog. Petrozavodsk. Publishing house: KarRC RAS. 120 p. [In Russian]. Rumyantsev E. A., Permyakov E.V. 1994. Fish parasites of the Pyaozero. Shulman, SS. (ed.). Ecological parasitology. Petrozavodsk. KarRC RAS Publishing House. 53—78. [In Russian]. Rumyantsev E. A., Permyakov E. V., Drizhachenko E. L. 1979. The parasite fauna of the Pyaozero fish. Proceedings ofVNIIPRKH. M. Issue. 23: 149—172. [In Russian]. Rumyantsev E. A., Shulman B. S., Ieshko E. P. 2001. Parasite fauna of the fishes of the Ladoga Lake. E. P. Ieshko (ed.). Ecological and parasitological studies of animals and plants in the European North. Petrozavodsk. Publishing house KarRC RAS. 25—29. [In Russian]. Ryb ak V. F. 1982. The formation of the parasite fauna of the fish of the Vygozero reservoir. S. S. Shulman (ed.). Ecology of parasitic organisms in biogeocenoses of the North. Pet- rozavodsk. Publishing house: Kar. Branch of the Academy of Sciences of the USSR. 59—72. [In Russian]. Sendek D. S., Studenov 1.1., Sherstkov V. S., Novoselov A. P., Konova- lov A. F. 2005. Genetic differentiation of smelt fishes of the genus Osmerus (Osmeri- dae, Salmoniformes) in the European North of Russia. Proceedings of KarRC RAS. Biogeography. Salmonids of East Fennoscandia. Petrozavodsk. KarRC RAS Publishing House. 148—157. [In Russian]. Skurikhina L. A., Kuhlevsky A. D., Oleynik A. G., Kovpak N. E. 2010. Analysis of phylogenetic relations of smelt fish (Osmeridae) according to the variability of the cy- tochrome b gene. Genetics. 46 (1): 79—91. [In Russian]. Smirnova-Stefanovskaya A. F. 1967. Morphological and biologoecological characte- ristics of the smelt of the lakes of Karelia. Author's abstract. Dis... cand. Biol. Sciences. Petrozavodsk. 30 p. [In Russian]. Voigt H. R. 1975. A checklist of the parasites on the smelt (Osmerus eperlanus). Särtryckur Finska Vetenskaps-Societetens Parasitologiska institut. Tiedoksianto. Information. 14: 28—40. Volodin V.M., Ivanova M.N. 1973. Size-age variability of smelt Osmerus eperlanus (L.). Journal of Ichtyology. 13 (2): 875—887. [In Russian].

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