MOLLUSCS ON CHARACEAE IN AN OLIGOTROPHIC HAÑCZA LAKE (NE POLAND)

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FOLIA MALACOLOGICA ISSN 1506-7623 The Association of Polish Malacologists & Faculty of Biology, Adam Mickiewicz University Poznañ 1999 Vol. 7(1): 47 50 MOLLUSCS ON CHARACEAE IN AN OLIGOTROPHIC HAÑCZA LAKE (NE POLAND) ANDRZEJ KO ODZIEJCZYK Department of Hydrobiology, Institute of Zoology, University of Warsaw Banacha 2, 02-097 Warszawa, Poland (e-mail: kol@hydro.biol.uw.edu.pl) ABSTRACT: In the littoral of an oligotrophic Hañcza Lake molluscs were the second most abundant group (next to Asellus aquaticus (L.)) of invertebrate macrofauna on Characeae (17% 34% total abundance). Thirteen taxa were found, with a distinct dominance of Dreissena polymorpha (Pall.); in some sites the proportion of Valvata cristata O. F. Müll. or the genus Pisidium was considerable. A rare relict Marstoniopsis scholtzi (Schm.) was sporadic. KEY WORDS: Mollusca, littoral, Characeae, oligotrophy, Dreissena polymorpha, Marstoniopsis scholtzi INTRODUCTION In low-trophy lakes Characeae are the dominant component of submerged macrophytes. They provide a very good substratum for invertebrate macrofauna; occurring in large patches and being present in the littoral throughout the year, they are habitable even when plants of annual oveground shoots die off (PEREYRA-RAMOS 1981, RZÊDKOWSKA 1987, OZIMEK 1997). Their significance for settling of larvae of Dreissena polymorpha (LEWANDOWSKI 1982) is especially great, and they harbour the zebra mussel in large numbers (PEREYRA-RAMOS 1981), compared with other species of submerged macrophytes (LEWANDOWSKI &OZIMEK 1997). With increasing trophy, a disappearance of Characeae takes place (LACHAVANNE 1985, KOWALCZEWSKI &OZIMEK 1993). The Hañcza Lake is one of the very few remaining large lakes in north-eastern Poland where these plants occur in abundance. Because of its specificity and unique character, since 1963 the Hañcza Lake has been under a partial nature reserve protection (R KOWSKI 1989); it has been also placed on the world s list of protected lakes (LUTHER &RZÓSKA 1971). In spite of this it was intensely studied only with respect to morphometry and water chemistry, whereas its fauna, including molluscs, is very poorly known. The objective of this study was a preliminary estimate of the species composition and density of malacofauna inhabiting Characeae in the littoral of the Hañcza Lake. STUDY AREA AND METHODS The Hañcza Lake is located in the Nemen river catchment area, in a lake district called Pojezierze Wschodniosuwalskie a part of a larger Lithuanian Lakeland. It is the deepest lake of the Central European Lowlands (maximum depth 108.5 m, mean depth 38.7 m, surface area 311.4 ha), and of the lowest trophy (oligo- or mesotrophic, ILLBRICHT- ILKOWSKA &WIŒNIEWSKI 1994) of our lowland lakes, with I class water quality (CYDZIK et al. 1995). It is characterized by a stony littoral (litholittoral), rarely found in lowland lakes, almost along its whole shoreline. Over a considerable part of the shore tightly

48 Ko³odziejczyk A. packed boulders form a layer over 2 m thick (RÜHLE 1932); the boulders are usually covered by a thick crust of algae, or overgrown with dense underwater meadows of Characeae which clearly dominate among submerged macrophytes. Emerged macrophytes are the reed (Phragmites australis (Cav.) Trin. ex Steudel) occurring in places; among macrophytes of floating leaves, the yellow water-lily (Nuphar luteum (L.) Sm.) is found sporadically. Samples of Characeae were collected at the beginning of September 1997 in the littoral of the Hañcza Lake, in four sites spaced evenly around the lake (Fig. 1), five in each site, from the depth of ca. 0.5 1.0 m. The fresh weight of the samples ranged from 90 to 212 g. The samples were washed on a benthos sieve of 1 mm mesh size and sorted macroscopically. Molluscs were sorted out, snails were identified according to PIECHOCKI S (1979) key; species of the subgenus Radix were determined based on the colouration of mantle and sole (JACKIEWICZ 1993, 1998). Only a small specimen of the subgenus Galba has remained unidentified, while the pill clams (Sphaeriidae) were determined only to the generic level. N II 108,5 Czarna Hañcza III RESULTS IV A total of 2,679 mollusc specimens were collected in the Hañcza Lake. They constituted an important component of invertebrate macrofauna, being in most cases the second most abundant (next to Asellus aquaticus (L.) which formed from 31% to 66% at particular sites), or even dominant group. Depending on the site (Table 1), molluscs constituted on an average from 17% to 34% total abundance of invertebrate macrofauna, and in some samples their proportion was as high as 50%. The average density of molluscs in particular sites (Table 2) ranged from 73 to 139 individuals per 100 g fresh weight of plants, at a relatively low variability range. Representatives of 13 mollusc taxa were found in the Hañcza Lake (Table 3). Dreissena polymorpha (Pallas) had the highest frequency, being present in all the samples; it was followed by Bithynia tentaculata (Linnaeus); members of the genus Pisidium were fairly frequent. The frequency of occurrence of the remaining molluscs was clearly lower; the least frequent, i.e. found only in one sample each (a single specimen in each case), were Gyraulus albus (O. F. Müller) and Lymnaea (Galba) sp. The dominance structure was very clear in all the sites (Fig. 2). The distinct dominant of all the sites, D. polymorpha, constituted from 67% to 93% abundance of all molluscs. In site I, Valvata cristata O. F. Müller formed 27% total abundance, and in site II clams of the genus Pisidium 20%. The remaining dominance values did not exceed 5%, and in many cases the percentage of particular species did not reach even 1% total abundance. I Czarna Hañcza Fig. 1. Location of sampling sites in Hañcza Lake Table 1. Proportion of molluscs in the abundance of invertebrate macrofauna of Characeae in the littoral of Hañcza Lake Noof sampling Percentage of molluscs site mean range I 21 10 31 II 31 21 46 III 17 13 20 IV 34 19 50

Molluscs on Characeae in Hañcza Lake 49 Table 2. Density of molluscs on Characeae in the littoral of Hañcza Lake Noof sampling Density (indiv. 100 g -1 ) site mean range I 73 49 131 II 153 83 321 III 85 65 112 IV 139 71 214 Table 3. Frequency of particular mollusc taxa on Characeae in the littoral of Hañcza Lake NoTaxon Frequency (%) 1 Dreissena polymorpha (Pall.) 100 2 Bithynia tentaculata (L.) 90 3 Pisidium sp. 75 4 Physa fontinalis (L.) 40 5 Valvata cristata O.F. Müll. 35 6 Anisus contortus (L.) 30 7 Lymnaea (Radix) peregra (O.F. Müll.) 15 8 Armiger crista (L.) 15 9 Planorbis carinatus O.F. Müll. 10 10 Sphaerium sp. 10 11 Marstoniopsis scholtzi (Schm.) 10 12 Gyraulus albus (O.F. Müll.) 5 13 Lymnaea (Galba) sp. 5 Fig. 2. Dominance structure of molluscs on Characeae in the littoral of Hañcza Lake (number of taxa given in upper row). Sampling sites as in Fig. 1. DISCUSSION Previous data on the malacofauna of the Hañcza Lake are very scanty. POLIÑSKI (1917, 1922) listed only four mollusc species from that lake, and KO ODZIEJCZYK (1994), during his qualitative studies on the littoral of lakes and rivers of the Suwalski Landscape Park, found there members of 10 taxa. Among the snails recorded by him, at present only Viviparus contectus (Millet), a bottom-dweller, only loosely associated with vegetation, was not re-found during the present study. Newly recorded mollusc species (Table 3) are Anisus contortus (Linnaeus), Armiger crista (Linnaeus) and Marstoniopsis scholtzi (Schmidt). The latter species, small and usually occurring at low abundance, was regarded as a glacial relict (POLIÑSKI 1917, 1922) or a North-European species (FALNIOWSKI 1987). In the waters of the Suwalski Landscape Park it was previously recorded (only empty shells) from the lakes Wodzi³ki, Kamendu³ and Przechodnie (KO ODZIEJCZYK 1994). In the nearest vicinity it was sporadically found in the lakes Wigry (POLIÑSKI 1917, 1922, LEWANDOWSKI 1992, KO ODZIEJCZYK in press), Krzywe (POLIÑSKI 1917, 1922), Pierty (LEWANDOWSKI 1992) and Bia³e Wigierskie (LEWANDOWSKI 1992, KO ODZIEJCZYK 1996). FALNIOWSKI (1987) lists this species for Suwa³ki lakes, not mentioning any exact localities. The pattern of occurrence of molluscs on Characeae in the Hañcza Lake departs in several respects from what is observed in some low-trophy lakes. The abundance very clearly exceeds the values reported, in the same month, for the lakes Majcz Wielki (PEREYRA-RAMOS 1981) and Bia³e Wigierskie (KO ODZIEJCZYK 1996). The low proportion (Fig. 2) of Bithynia tentaculata which constitutes a considerable percentage of the malacofauna of both these lakes and dominates in a mesotrophic lake Garbaœ

50 Ko³odziejczyk A. Du y (lake district Pojezierze E³ckie), where it constituted 84% malacofauna on Characeae (own, unpublished results), is alsoatypical. The disappearance of this species is usually associated with increasing eutrophication (PIECZYÑSKA et al. in press). Such a high proportion of Dreissena polymorpha (Fig. 2) as in the Hañcza Lake, is alsoobserved in the lake Majcz Wielki, while its proportion is low in the lakes Bia³e Wigierskie and (especially) Garbaœ Du y (only 5%). The high percentage of molluscs in the macrofauna (Table 3) is rather typical of low-trophy lakes; similar is the case of the low percentage of members of the subgenus Radix (PIECZYÑSKA et al. in press). The studies presented in this paper have provided a preliminary characteristics of the malacofauna on Characeae in the Hañcza Lake. The lake is a reservoir of the lowest trophy, hence it can be regarded as a reference point during studies in other water bodies. Further, more extensive studies on the malacofauna of various zones of this lake will follow. ACKNOWLEDGEMENTS I am grateful toms. AGNIESZKA TWARÓG for her help with processing the material. REFERENCES CYDZIK D., KUDELSKA D., SOSZKA H. 1995. Atlas stanu czystoœci jezior w Polsce badanych w latach 1989 1993. Pañstwowa Inspekcja Ochrony Œrodowiska, Biblioteka Monitoringu Œrodowiska, Warszawa. FALNIOWSKI A. 1987. Hydrobioidea of Poland (Prosobranchia: Gastropoda). Folia Malacol. 1: 1 122. HILLBRICHT-ILKOWSKA A., WIŒNIEWSKI R. J. 1994. Zró nicowanie troficzne jezior Suwalskiego Parku Krajobrazowego i jego otuliny stan obecny, zmiennoœæ wieloletnia, miejsce w klasyfikacji troficznej jezior. In: Jeziora Suwalskiego Parku Krajobrazowego zwi¹zki z krajobrazem, stan eutrofizacji, kierunki ochrony (HILLBRICHT-ILKOW- SKA A., WIŒNIEWSKI R. J., eds), pp. 181 200. Zesz. Nauk. Komitetu Cz³owiek i Œrodowisko PAN 7. JACKIEWICZ M. 1993. Die Mantelpigmentation als Diagnosemerkmal bei Schlammschnecken (Gastropoda, Pulmonata: Lymnaeidae). Malak. Abh. 16: 165 172. JACKIEWICZ M. 1998. European species of the family Lymnaeidae (Gastropoda: Pulmonata: Basommatophora). Genus 9: 1 93. KO ODZIEJCZYK A. 1994. Miêczaki s³odkowodne Suwalskiego Parku Krajobrazowego. In: Jeziora Suwalskiego Parku Krajobrazowego zwi¹zki z krajobrazem, stan eutrofizacji, kierunki ochrony (HILLBRICHT-ILKOWSKA A., WIŒ- NIEWSKI R. J., eds), pp. 181 200. Zesz. Nauk. Komitetu Cz³owiek i Œrodowisko PAN 7. KO ODZIEJCZYK A. 1996. Makrofauana bezkrêgowa (ze szczególnym uwzglêdnienim Gastropoda) na wybranych makrofitach zanurzonych w litoralu Jeziora Bia³e Wigierskie. Parki Narod. i Rez. Przyrody 14: 77 88. KO ODZIEJCZYK A. (in press). Miêczaki litoralu jeziora Wigry. In: (ZDANOWSKI B., ed.). Zesz. Nauk. Komitetu Cz³owiek i Œrodowisko PAN. KOWALCZEWSKI A., OZIMEK T. 1993. Further long-term changes in the submerged macrophyte vegetation of the eutrophic lake Miko³ajskie (North Poland). Aquatic Botany 46: 341 345. LACHAVANNE J.-B. 1985. The influence of accelerated eutrophication on the macrophytes of Swiss lakes: Abundance and distribution. Verh. Internat. Verein. Limnol. 22: 2950 2955. LEWANDOWSKI K. 1982. The role of early developmental stages in the dynamics of Dreissena polymorpha (Pall.) (Bivalvia) population in lakes. II. Settling of larvae and the dynamics of numbers of settled individuals. Ekol. pol. 30: 223 286. LEWANDOWSKI K. 1992. Wystêpowanie i rozmieszczenie miêczaków, ze szczególnym uwzglêdnieniem ma³ a Dreissena polymorpha (Pall.) w litoralu kilku jezior Wigierskiego Parku Narodowego. In: Jeziora Wigierskiego Parku Narodowego. Stan eutrofizacji i kierunki ochrony (ZDA- NOWSKI B., ed.), pp. 145 151. Zesz. Nauk. Komitetu Cz³owiek i Œrodowisko PAN 3. LEWANDOWSKI K., OZIMEK T. 1997. Relationship of Dreissena polymorpha (Pall.) to various species of submerged macrophytes. Pol. Arch. Hydrobiol. 44: 457 466. LUTHER H., RZÓSKA J. (eds) 1971. Project Aqua inland water proposed for conservation: IBP Handbook Nr. 21, Blackwell Scientific Publ., Oxford-Edinburgh. OZIMEK T. 1997. Submerged macrophytes as a substrate for Dreissena polymorpha (Pall.) in five lakes of the Jorka river watershed. Pol. Arch. Hydrobiol. 44: 445 455. PEREYRA-RAMOS E. 1981. The ecological role of Characeae in the lake littoral. Ekol. pol. 29: 167 209. PIECHOCKI A. 1979. Miêczaki (Mollusca). Œlimaki (Gastropoda). Fauna s³odkowodna Polski 7. PWN, Warszawa. PIECZYÑSKA E., KO ODZIEJCZYK A., RYBAK J. I. (in press) The response of littoral invertebrates to eutrophication-linked changes on plant communities. Hydrobiologia. POLIÑSKI W. 1917. Materya³y do fauny malakozoologicznej Królestwa Polskiego, Litwy i Polesia. Prace Tow. Nauk. Warsz. III, Wydz. nauk. mat. i przyr. 27: 1 130. POLIÑSKI W. 1922. O faunie miêczaków Ziemi Suwalskiej. Arch. Hydrob. i Ryb. 1: 37 43. R KOWSKI G. 1989. Suwalski Park Krajobrazowy. Wyd. PTTK Kraj, Warszawa. RÜHLE E. 1932. Jezioro Hañcza na Pojezierzu Suwalskim. Wiad. S³u by Geograf. 4: 1 26. RZÊDKOWSKA L. 1987. Wykorzystanie roœlin jako pod³o y przez makrofaunê bezkregow¹ w litoralu jeziornym w okresie zlodzenia. Praca magisterska, Uniwersytet Warszawski. received: December 15th, 1998

accepted: January 15th, 1999 51