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Malacofauna of the Holsteinian lake deposits at Hrud II (Eastern Poland) and its palaeoecological significance

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Malacofauna of the Holsteinian lake de pos its at Hrud II (East ern Po land) and its palaeo eco logi cal sig nif i cance

Marcin SZYMANEK

Szymanek M. (2012) – Malacofauna of the Holsteinian lake de pos its at Hrud II (East ern Po land) and its palaeo eco logi cal sig nif i cance.

Geol. Quart., 56 (1): 117–126. Warszawa.

Mol lusc-bear ing de pos its at Hrud II (East ern Po land) ac cu mu lated in the west ern part of a palaeolake of Holsteinian age (MIS 11). The fau nal as sem blage is typ i cal of fresh wa ter en vi ron ments and pre sum ably rep re sents a part of the inter gla cial cli ma tic op ti mum (Carpinus–Abies Zone). On the ba sis of its var ied com po si tion, the evo lu tion of the wa ter body is de scribed. Re in ter pre ta tion of the data from the east ern part of the lake (Hrud I) and com bin ing of the re sults from both sites en able a wider palaeo eco logi cal re con struc tion.

Fluc tu a tions in lake level, wa ter dy nam ics and changes in the aquatic veg e ta tion are in ferred from quan ti ta tive re la tions be tween se lected molluscs, es pe cially Lithoglyphus jahni, Valvata piscinalis and Bithynia tentaculata, which pre vail in the de pos its in ves ti gated. A pre - dom i nance of Valvata piscinalis in di cates a rise in wa ter level, whereas the com mu ni ties with abun dant Bithynia opercula are typ i cal of a more shal low lake with rich reed fields. Ame lio ra tion of the trophic con di tions be tween the pre-op ti mal and op ti mal part of the Holsteinian Inter gla cial can also be recognized.

Marcin Szymanek, Fac ulty of Ge ol ogy, Uni ver sity of War saw, Żwirki i Wigury 93, 02-089 Warszawa, Po land, e-mail:

m.szymanek@uw.edu.pl (re ceived: Oc to ber 25, 2011; ac cepted: De cem ber 19, 2011).

Key words: Qua ter nary, Holsteinian, lake de pos its, molluscs, palaeoenvironment.

INTRODUCTION

Lac us trine de pos its with molluscs were firstly de scribed in the vi cin ity of Hrud near Biała Podlaska (East ern Po land) at the be gin ning of the 1990s (Lindner et al., 1991). Their lo ca tion, known as Hrud I, is con nected with the east ern part of the de - pres sion be tween Ossówka and Hrud (Fig. 1), which is the shore zone of a palaeolake that ex isted in this area in the Holsteinian Inter gla cial (Lindner et al., 1991; Nitychoruk, 1994) cor re - spond ing to Ma rine Iso tope Stage 11 (MIS 11; Nitychoruk et al., 2005, 2006). The lake was nar row (up to 1 km) and sev eral kilo - metres long of a depth that reached over a dozen metres in the area of Hrud (Lindner and Marciniak, 1997; Nitychoruk, 2000, 2005). Car bon ate gyttja and lake marl ac cu mu lated in its cen tral part (Fig. 2). In the shore zone, silts, sandy silts as well as sands with fine gravel, abun dant molluscs and lo cally with interbeds of gyttja were de scribed and sub jected to fau nal and palaeobotanical anal y ses which con firmed their Holsteinian age (Lindner et al., 1991; Skompski, 1996; Krupiński, 2000). Dur - ing fur ther in ves ti ga tions mol lusc-bear ing de pos its were also dis cov ered in the west ern part of the lake and termed the Hrud II site, though molluscs were only briefly men tioned (Nitychoruk,

1994; Fig. 2). Al though not as well stud ied as the east ern part of the lake, the pre lim i nary re sults show dis tinct dif fer ences be - tween the mol lusc as sem blages at Hrud I and II (Szymanek, 2011a, b). The clear est dif fer ence is a greater abun dance of Viviparus diluvianus and fewer Bithynia tentaculata at Hrud II in com par i son with Hrud I. The newly col lected ma te rial is abun - dant, and the pol len as well as the snails Viviparus diluvianus and Lithoglyphus jahni are typ i cal of the Holsteinian Inter gla cial in Po land (Szymanek, 2008a, 2011a).

The pres ent pa per de scribes in de tail the molluscs from Hrud II and con sid ers their en vi ron men tal sig nif i cance in re la tion to the palaeo eco logi cal in ter pre ta tion made of the east ern part of the lake (Lindner et al., 1991). Palaeo eco logi cal con di tions for the Hrud palaeolake, based on the molluscs, are re as sessed.

MATERIAL AND METHODS

The well-pre served and nu mer ous mol lusc shells at Hrud II ac cu mu lated in fine-, me dium- and vari-grained sands ca.

1.3 m thick cov ered by a thin layer of deluvial de pos its. In this study eight sam ples at 10 cm in ter vals were taken for malacological anal y sis. They were col lected from a small ex ca -

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va tion in the depth in ter val 0.8–1.6 m. Ap prox i mately 3 litres of sed i ment per sam ple were wet-sieved us ing a 0.5 mm mesh.

Mol lusc shells and their frag ments were then picked, iden ti fied and counted. Some in com plete spec i mens, es pe cially thin-walled Pisidium bi valves were de ter mined only to ge nus level. Stan dard malacological meth ods es tab lished by Ložek (1964), Alexandrowicz (1987) and Alexandrowicz and Alexandrowicz (2011) were ap plied. Firstly the molluscs were listed ac cord ing to their en vi ron men tal re quire ments (Ta ble 1).

Three eco log i cal groups were dis tin guished at Hrud II: spe cies of tem po rary wa ter bod ies – 10, spe cies of per ma nent wa ter

bod ies of stag nant wa ters – 11 and spe cies of flow ing wa ters – 12. Dur ing the in ter pre ta tion sup ple men tary classes af ter Ložek (1964, 1976, 1982) mod i fied ac cord ing to Körnig (1966), Piechocki (1979) and Skompski and Makowska (1989) were also con sid ered (Ta ble 1). In ad di tion, for all sam ples, malacological spec tra of spe cies (MSS) and spec i mens (MSI;

Fig. 3) as well as a sim pli fied malacological di a gram (Fig. 4) show ing changes in the as sem blage were con structed. Sim i lar fig ures (Figs. 5 and 6) were drawn for the Hrud I site, to il lus - trate dif fer ences in mol lusc com po si tion and eco log i cal changes in the wa ter body. In this case the data of Lindner et al.

(1991) and Skompski (1996) were used.

MOLLUSCS AND ENVIRONMENTAL CHANGES

HRUD II

The mol lusc as sem blage at Hrud II com prises 25 taxa – 9 spe cies and 1 ge nus of snails as well as 13 spe cies and 2 gen era of bi valves, with a to tal of 19690 spec i mens (Ta ble 1). The num ber of both taxa and spec i mens var ies from 14 to 20 and from 1193 to 3766 per sam ple re spec tively. De spite some fluc - tu a tions it drops grad u ally to wards the up per part of the sec tion which may sug gest a slight de te ri o ra tion of the con di tions.

Only in sam ple 2 (0.9–1.0 m) was a dis tinct in crease in num ber of spec i mens ob served (Fig. 3).

All taxa re cog nised link the as sem blage with fresh wa ter en - vi ron ments (Ta ble 1). Spe cies char ac ter is tic of per ma nent wa - ter bod ies of stag nant wa ters (eco log i cal group 11) pre dom i - nate but most of them can oc cur in both rivers and lakes.

Fig. 1. Lo ca tion sketch of the study area

Fig. 2. Geo log i cal cross-sec tion in the vi cin ity of Hrud II (af ter Nitychoruk, 1994, mod i fied) 1 – Sanian 2 Gla ci ation; 2, 3 – Holsteinian Inter gla cial; 4–7 – Odranian Gla ci ation; 8 – Wartanian Gla ci ation;

9 – Vistulian Gla ci ation; 10, 11 – Ho lo cene

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Among spe cies of per ma nent wa ter bod ies of var i ous size, abun dant Valvata piscinalis f. antiqua was re corded as well as Armiger crista f. nautileus, Acroloxus lacustris, Pisidium lilljeborgii which are rep re sented by sin gle spec i mens.

Molluscs which pre fer flow ing wa ters (eco log i cal group 12) such as Pisidium amnicum, Pisidium nitidum, Pisidium supinum and Unio pictorum may at tain 30% of all taxa (sam ple 5, 1.2–1.3 m) but in fact they ap pear in in sig nif i cant quan ti ties (Ta ble 1 and Fig. 3). They prob a bly rep re sent the wave af fected zone in lac us trine en vi ron ment. The lat ter is clearly ev i denced by the lac us trine form Valvata piscinalis f. antiqua (Piechocki, 1979). How ever, oc ca sional slowly flow ing wa ter is sug gested by Pisidium henslowanum at Hrud II (cf. Piechocki and Dyduch-Falniowska, 1993).

The mol lusc as sem blage in the Hrud II sec tion is dom i nated by three taxa – Valvata piscinalis, Lithoglyphus jahni and Viviparus diluvianus, al though not evenly. In the low est part of the pro file (depth 1.3–1.6 m) L. jahni pre vails and it is a main com po nent of the fauna. V. piscinalis, V. piscinalis f. antiqua as well as V. diluvianus are abun dant but only the first of these makes more than 10% of the as so ci a tion (Fig. 4). Gen er ally nu -

mer ous P. amnicum and P. nitidum point to rather strong wave ac tion. The lat ter did not sup port aquatic veg e ta tion as seen in a low con tent of spe cies liv ing on wa ter plants. The re stricted num ber of pul mo nates to gether with a dom i nance of prosobranch gas tro pods in di cates ac cu mu la tion be low 2 or 3 m wa ter depth (Alexandrowicz, 1987).

To wards the up per part of the sec tion pre dom i nance of L.

jahni de creases (sam ples 2–5, Fig. 4). It is still a sig nif i cant el e - ment of the com mu nity, but it is re placed by V. piscinalis and V.

piscinalis f. antiqua, in di cat ing some what deeper hab i tats (8–10 m). This is a typ i cally zone with a muddy sub stra tum and sparse veg e ta tion (Piechocki, 1979; Alexandrowicz, 1987;

Alexandrowicz, 2008). The as so ci a tion with V. piscinalis is ac - com pa nied by V. diluvianus. A scar city of pul mo nates is still ob served, how ever, some changes in veg e ta tion can be in ferred from the pro por tions of opercula of Bithynia tentaculata which ap pears in the up per most part of the suc ces sion in more sig nif i - cant amounts. Both the shells and opercula are of ten sorted in the lit to ral zone of wa ter bod ies and the ra tios be tween them, ex pressed by the Bithynia-in dex (BIN) = (opercula – shells)/(opercula + shells), are a guide to sed i men tary en vi ron -

I II Taxon Samples

1 2 3 4 5 6 7 8

10 WP Pisidium obtusale (Lamarck) 1

11 We Viviparus diluvianus (Kunth) 5 5 5 5 5 6 5 4

11 We Valvata piscinalis Müller 6 6 6 6 6 6 6 6

11 WL Valvata piscinalis f. antiqua Sowerby 5 5 5 5 5 5 5 5

11 We Lithoglyphus jahni Urbański 6 6 5 6 7 7 7 7

11 We Bithynia tentaculata (Linnaeus) (+operculum)

1 3

1 4

1 2

1 2

2 2

1 1

1

1 1

11 WL Lymnaea stagnalis (Linnaeus) 1 1 1 1

Lymnaea sp. 1 1 1 1 k 1

11 We Gyraulus albus Müller 1 3 1 1 1 2 1

11 WL Armiger crista f. nautileus (Linnaeus) 1

11 WL Acroloxus lacustris (Linnaeus) 1 1 1 1

11 We Pisidium henslowanum (Sheppard) 1 2 1 1 1 1 1 3

11 We Pisidium milium Held 1? 1

11 We Pisidium subtruncatum Malm 3 4 1 1 2 2 2 4

11 WL Pisidium lilljeborgii Clessin 1?

11 We Pisidium casertanum (Poli) 3 4 2 2 2 2 3 3

11 We Pisidium casertanum f. pon der osa Stelfox 3 3 2 2 1 1 2 3

11 We Pisidium moitessierianum Paladilhe 1 1 1 1 1 3 3

12 Wc Unio pictorum (Linnaeus) 1

12 We Unio tumidus Philipsson 1 1 1

12 Unio sp. 1 1 k 1

12 Wc Pisidium amnicum (Müller) 1 1 2 3 3 4 3

12 Wc Pisidium supinum A. Schmidt 1?

12 We Pisidium nitidum Jenyns 3 4 2 2 2 2 3 4

Pisidium sp. 3 4 2 3 3 3 3 4

I – eco log i cal groups (af ter Ložek, 1964; Alexandrowicz, 1987): 10 – spe cies of tem po rary wa ter bod ies, 11 – spe cies of per ma nent wa ter bod ies of stag - nant wa ters, 12 – spe cies of flow ing wa ters; II – sup ple men tary eco log i cal sym bols (af ter Ložek, 1964, 1976, 1982; Körnig, 1966; Piechocki, 1979;

Skompski and Makowska, 1989): Wc – spe cies pre fer ring flow ing wa ters with weak cur rents, We – spe cies pres ent both in rivers and lakes, in stag nant and flow ing wa ters, WL – spe cies of per ma nent wa ter bod ies of var i ous size, WP – molluscs of ep i sodic, pe ri od i cally dry ing out wa ter bod ies; num ber of spec i - mens: 1 – 1–3, 2 – 4–9, 3 – 10–31, 4 – 32–99, 5 – 100–316, 6 – 317–999, 7 – more than 1000, k – a few frag ments of shell

T a b l e 1 Malacofauna of the Hrud II site

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Fig. 4. Sim pli fied malacological di a gram (D) and changes of the Bithynia-in dex (BIN) at Hrud II For ex pla na tions see Fig ure 3

Fig. 3. Malacological com po si tion of the Hrud II pro file

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Fig. 6. Sim pli fied malacological di a gram (D) and changes of the Bithynia-in dex (BIN) at Hrud I (based on data pub lished by Lindner et al., 1991)

For ex pla na tions see Fig ure 5

Fig. 5. Malacological com po si tion of the Hrud I pro file (based on data pub lished by Lindner et al., 1991) For ex pla na tions see Fig ure 3

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I II Taxon Samples

1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20 21 22

8 MD Succinea oblonga

Draparnaud 2

9 WD Succinea

putris-elegans 1

10 WP Pisidium obtusale

(Lamarck) 1

11 We Viviparus diluvianus

(Kunth) 1 k 1d 1 1k 1k 1d 2d 1k d 1d 1 1 2

11 We Valvata piscinalis

Müller 3 3 5 4 4 4 4 4 1 3 3 3 4 4 3 4 2 1 1

11 WL Valvata piscinalis f.

antiqua Sowerby 1 1d 1d 2d 1d 3 3 2 3 k 1k 3 3 3 3 3 3 3 2 2 3

11 Wp Valvata cristata Müller 1 1 1 1

11 We Lithoglyphus jahni

Urbański 1 1 1 1 1 1 1 1 1 2 3d 4 2 2 2 2 3 3 4 3

11 We

Bithynia tentaculata (Linnaeus) (+operculum)

3 4

2 3

3 4

4 5

3

4 2 2

1

1 1

3 4

1

1 1 1

1

2 1 2

Lymnaea (Ra dix) 2 1 3 1

Lymnaea sp. 1 k

11 Wp Anisus vorticulus

(Troschel) k

11 We Gyraulus albus Müller 1 1 1 1 1 1 1 1

11 WL Armiger crista f.

nautileus (Linnaeus) 1 2 1

11 Acroloxus sp. 1 1 2 1 1 1 1 1 1

11 We Sphaerium corneum

(Linnaeus) d d k d k k k k k

Sphaerium sp. d d d d k k k k k k d k k

11 We Pisidium henslowanum

(Sheppard) ? ? 1?

11 We Pisidium milium Held ? 1?

11 We Pisidium subtruncatum

Malm 1? ? 1 1 3 2 1

11 WL Pisidium lilljeborgii

Clessin 1

11 We Pisidium casertanum

(Poli) 1 4 3 2 3 2 1 1 1 1 3 1k 1 1 1

11 We Pisidium casertanum f.

pon der osa Stelfox 1 1 1 1

11 We

Pisidium moitessierianum

Paladilhe 1 1 2 1 1 2 2 3 3 2 2 1 2 2 1

11 Pisidium parvulum

Clessin 2 2 3 1 2 3 3 3 2 3 2 1 1 1

12 Unio sp. k k k k k k d d d k d d d d k

12 Wc Pisidium amnicum

(Müller) 1

12 Wc Pisidium supinum

A. Schmidt 1 1 1 1 ? ? ? ?

12 We Pisidium nitidum

Jenyns 1 2 2 1 1

Pisidium sulcatum

(S. V. Wood) ?

Pisidium sp. d d 1 ?

8 – mesophile spe cies of mod er ately moist en vi ron ment; 9 – spe cies of very moist hab i tats; MD – mesophile spe cies of hu mid hab i tats, WD – snails of swamps, flooded mead ows and shores of wa ter bod ies, Wp – molluscs of per ma nent, shal low, in ten sively over grown wa ter bod ies; d – shell de tri tus; other ex pla na tions as in Ta ble 1

T a b l e 2 Malacofauna of the Hrud I site (based on Lindner et al., 1991 – mod i fied)

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ment. The opercula usu ally ac cu mu late on the bot tom in the reed zone and their dom i na tion is showed by the value of the in dex close to +1, while as so ci a tions com posed only of shells (BIN = –1) ap pear abun dantly along the shores (Steenberg, 1917; S. W. Alexandrowicz, 1999). The com mu nity at Hrud II is clearly en riched in Bithynia opercula and the Bithynia-in dex ris ing from 0.33 to 0.93 in di cates pro gres sive over grow ing of the lake by reed and bullrush (Alexandrowicz and Sanko, 1997; W. P. Alexandrowicz, 1999, 2004, 2008). These changes, pos si bly con nected with shallowing of the wa ter body and/or ame lio ra tion of trophic con di tions, are ac com pa nied by a de crease in a con tent of P. amnicum which can barely tol er - ate such en vi ron ment (Piechocki and Dyduch-Falniowska, 1993; Ta ble 1 and Fig. 4).

The molluscs at Hrud II have a wide cli ma tic tol er ance, how ever, from oc cur rence of e.g., Viviparus diluvianus, Lithoglyphus jahni, Acroloxus lacustris and Pisidium moitessierianum a tem per ate cli mate may be de duced. This is in agree ment with the re sults of pol len anal y sis, in di cat ing the warm phase of the Holsteinian Inter gla cial, prob a bly the Carpinus–Abies Zone, ex pressed in the sec tion by high fre - quen cies of oak, al der, fir, ha zel and horn beam (Szymanek, 2008a, 2011a).

HRUD I

Malacological in ves ti ga tions at Hrud I were con ducted on 22 sam ples (depth 0.8–5.2 m) taken from the bore hole HR-70 (Lindner et al., 1991; Skompski, 1996). The mol lusc as sem blage con sists of 31 taxa – 14 of snails and 17 of bi valves, rep re sented by over 2100 spec i mens. It is in gen eral rich and di verse, how - ever, many taxa ap pear as in di vid ual spec i mens. In many cases only a few frag ments of shells or shell de tri tus are pres ent, thus it is dif fi cult to de ter mine pre cisely the real abun dance of spec i - mens (Ta ble 2). Pre sum ably it changes from 23 to 366 per sam - ple, whereas the num ber of taxa is be tween 7 and 16 with some dis tinct fluc tu a tions ob served in the pro file (Fig. 5).

Ac cord ing to Skompski (Lindner et al., 1991; Skompski, 1996) the com mu nity is typ i cal of a lake with pos si ble over - flow or of a lit to ral zone with wave ac tion. The lat ter is sug - gested by the pres ence of Pisidium parvulum. The palaeoclimate has been de scribed as mild (Lindner et al., 1991;

Skompski, 1996). The gas tro pod fauna and the bi valves were in ter preted sep a rately. Two phases were dis tin guished in the de vel op ment of snails. The first has a high con tent of Lithoglyphus jahni and Viviparus diluvianus (sam ples 12–22, depth 3.0–5.2 m) and the sec ond is dom i nated by Bithynia tentaculata (sam ples 1–10, depth 0.8–2.8 m). Non-si mul ta - neous oc cur rence of these spe cies may be ex plained by changes of wa ter acid ity as B. tentaculata does not tol er ate an acidic en vi ron ment (Piechocki, 1979; Skompski, 1996). Ac - cord ing to Skompski (1996) the chem i cal com po si tion of the wa ter, cli mate or other un de ter mined fac tors may also be re - spon si ble for the lim ited con tent of V. diluvianus in the up per part of the pro file. Ex pan sion of bi valves was char ac ter ized of a phase with Pisidium moitessierianum, P. parvulum and the more or less con stant ap pear ance of Unio sp. (sam ples 7–22, depth 2.0–5.2 m) as well as by a phase of Pisidium casertanum

dom i nance (sam ples 1–6, depth 0.8–2.0 m; Lindner et al., 1991; Skompski, 1996).

As at the Hrud II site, spe cies in hab it ing both stag nant and flow ing wa ters are pres ent. Molluscs from eco log i cal group 11 pre vail. Reophile spe cies (group 12) may at tain 20% of the as - sem blage, al though only in sam ples 7, 8, 11 (depth 2.0–2.2 m;

2.2–2.4 m; 2.8–3.0 m) do they oc cur in quite con sid er able amounts (10–15% of the as sem blage), sug gest ing some wa ter move ment. In most cases they make no more than 3% of the com mu nity and are ab sent from sam ples 1 (0.8–1.0 m), 3 (1.2–1.4 m) and 5 (1.6–1.8 m) which points to a lack of the over - flow and/or a very calm in shore zone of the lake (Fig. 5). The lat - ter was prob a bly quite densely over grown by reeds as in di cated by high val ues of the Bithynia-in dex (0.46–0.77; Fig. 6).

As men tioned above, Bithynia tentaculata is the main com - po nent of the fauna in the up per most part of the sec tion. The lower one is dom i nated by Lithoglyphus jahni. Valvata piscinalis is also very abun dant; how ever, it dis ap pears in some sam ples (Fig. 6). It is worth not ing that de crease in its num ber usu ally co - in cides with greater amounts of B. tentaculata (Fig. 6), im ply ing pos si ble changes in wa ter level. While V. piscinalis of ten in hab - its deeper parts of the lake, for B. tentaculata a depth of 0.7–1.8 m is op ti mal (Piechocki, 1979; S. W. Alexandrowicz, 1987, 1999; Alexandrowicz, 2008). In the up per part of the sec - tion a bog bi valve Pisidium obtusale (eco log i cal group 10) as well as a cou ple of spe cies of land snails – Succinea putris-elegans and Succinea oblonga oc cur (Lindner et al., 1991). The first one rep re sents eco log i cal group 9, i.e. spe cies of very moist hab i tats, the sec ond is a mesophile snail of mod er - ately moist en vi ron ment (eco log i cal group 8). How ever, they are in sig nif i cant com po nents of the as so ci a tion (Ta ble 2).

Other groups of an i mals (ostracods, fishes, ro dents, in sects) have also been de scribed from Hrud I but as at Hrud II where fishes and ro dents are pres ent (Szymanek, 2008a) they do not in gen eral strengthen the in ter pre ta tion. Only the ostracod fauna in di cates a few stages of de vel op ment from a deeper to a rel a tively more shal low wa ter body (Lindner et al., 1991).

No palaeobotanical anal y ses have been made in the HR-70 pro file, how ever, Lindner et al. (1991) cor re late the suc ces sion with those dis tin guished in the nearby HR-53 and HR-54 pro - files (a few hun dred metres to the SE), where pol len and di a - toms were in ves ti gated. The cor re la tion can not be di rect and un equiv o cal, but it may be as sumed that the mol lusc as sem - blage rep re sents the older part of the Holsteinian Inter gla cial prob a bly cov er ing the in ter val of dom i nance of pine-birch for - ests with spruce and larch, of spruce for ests and of the phase of yew-pine for ests with spruce and al der. Un for tu nately, based on the avail able ma te rial, more de tailed in ter pre ta tion is im pos - si ble. Di a toms in di cate an oligo-mesotrophic lake, ame lio ra tion of the trophic con di tions and low er ing of the wa ter level (Lindner et al., 1991; Lindner and Marciniak, 1997, 1998).

DISCUSSION

A wa ter body of the Holsteinian age that ex isted in the vi cin ity of Hrud was in hab ited by the rich mol lusc fauna. It was dif fer en ti - ated into west ern (Hrud II sec tion) and east ern (Hrud I pro file)

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parts of the ba sin and evolved dur ing its de vel op ment. Changes in the as sem blages may have been ei ther syn chro nous and of lo cal or i gin or they may re flect evo lu tion of fresh wa ter en vi ron ments over a lon ger pe riod. It should be noted, how ever, that some changes may not be con nected with ecol ogy but rather re sult from dif fer ent sam pling meth ods used at Hrud I and II, hin der ing the in - ter pre ta tion. Al though the to tal vol ume of sam ple ma te rial de rived from the bore hole HR-70 is not given (Lindner et al., 1991) it was un doubt edly con sid er ably smaller than that col lected in the Hrud II ex ca va tion. This af fects in par tic u lar the abun dance of the as - sem blages, thus in cor re la tion the per cent age con tent of taxa and spec i mens should be emphasised in stead of their num bers. Com - ment is also needed on the ap pear ance of Pisidium parvulum Clessin, abun dant at Hrud I and ab sent at Hrud II. Ac cord ing to Boettger (1961) this is a syn onym of Pisidium hibernicum Westerlund, whereas Kuiper (1965) treats P. parvulum “as a com - pos ite spe cies” syn on y mous with P. obtusale (Kuiper et al., 1989). In the lit er a ture also P. parvulum Wood ward can be find and this name ap pears in synonomy of Pisidium moitessierianum (Piechocki, 1989). Bas ing on pic tures pre sented by Skompski (1996) the pres ence of P. hibernicum at Hrud I can be in ferred, but it is not cer tain. It seems, how ever, that an in ter val of abun dance of that spe cies was not re corded at Hrud II.

A few phases of the fau nal de vel op ment were dis tin guished in the pro files de scribed, ex pressed mostly by var i ous re la tions be tween Lithoglyphus jahni, Valvata piscinalis and Bithynia tentaculata. They show mod er ately dy namic changes in the mol lusc com mu ni ties which mainly re flect en vi ron men tal con - di tions. Some cli mate in flu ences can not be ex cluded, but the wide cli ma tic tol er ance of most spe cies lim its the palaeoclimatic in for ma tion that may be ob tained. Al though the pop u la tions share some sim i lar i ties it ap pears that they ex isted at dif fer ent times and re cord suc ces sive stages of the lake evo - lu tion as shown by the pol len data of the Hrud I (Lindner et al., 1991) and Hrud II sec tions (Szymanek, 2008a, 2011a).

The mol lusc as sem blage from the east ern part of the lake (Hrud I) is older and prob a bly rep re sents a lon ger pe riod than the fauna found along its west ern bank (Hrud II). Ini tially it was dom i nated by L. jahni. Un for tu nately, en vi ron men tal in ter pre - ta tion is hin dered here by the re stricted data con cern ing the ecol ogy of this spe cies. It lived in lakes and rivers (Urbański, 1975; Skompski and Makowska, 1989) or only in rivers (Gittenberger et al., 2004; Kondrashov, 2007), but no de tailed bathymetric data are pre sented. Now a days Lithoglyphus naticoides (Pfeif fer) is most fre quent in shal low depths (0.2–1.2 m), mainly in fluviatile en vi ron ments, some times in lakes, and it avoids over grown stag nant wa ters (Piechocki, 1979). It is hard to es ti mate how much in com mon had the fos - sil snail with these hab i tats; how ever, such an in ter pre ta tion would be in con sis tent with the in for ma tion from ostracods, show ing a rel a tively deep wa ter body at that time (Lindner et al., 1991). The lat ter in ter pre ta tion is sup ported by the suc ceed - ing com mu nity, dom i nated by V. piscinalis, which usu ally in - hab its depths of ca. 8–10 m. The lake bathymetry was not con - stant. A pe ri odic deep en ing and shallowing of the lake pos si bly oc curred, as re flected in fluc tu a tions of V. piscinalis and B.

tentaculata con tents. De crease in the wa ter level co in cided with the growth of bul lrush and reeds, whereas a deeper ba sin of wider ex tent fa voured more in ten sive wave ac tion, which re -

stricted aquatic in shore veg e ta tion. The most dis tinct drop in the wa ter level and grad ual over grow ing of the lake was noted in the up per most part of the Hrud I pro file (a phase of yew dom - i na tion or later?). Very calm, to tally stag nant and prob a bly more eutrophic wa ters pre vailed at that time.

A youn ger stage of the lake de vel op ment is re corded in its west ern part; how ever, a hi a tus be tween the Hrud I and II sec - tions can not be ex cluded. The molluscs from the Hrud II site ex isted dur ing a phase of fir and horn beam pre dom i nance in for est com mu ni ties (Szymanek, 2008a, 2011a). Ac cord ing to Bińka (Bińka and Nitychoruk, 1995, 1996; Bińka et al., 1997) this is the cli ma tic op ti mum of the Holsteinian Inter gla cial. The com mu nity was again dom i nated by L. jahni, which was sub se - quently re placed by V. piscinalis. The lake be came deeper and some slight move ments of the wa ter ap peared. Higher in the suc ces sion a drop in wa ter level was com bined with re newed growth of bullrush and reeds along the shore. Better trophic con di tions can be also as sumed. The part of the lake re corded at Hrud II was per ma nently in hab ited by abun dant Viviparus diluvianus which oc curred in lim ited num ber at Hrud I. The warm and mild cli mate of the op ti mum was cer tainly fa vour - able for this (Szymanek et al., 2005; Szymanek, 2008a, b, 2011a). The prob lem is that sim i lar con di tions pre vailed dur ing the Taxus (yew) zone of the Holsteinian. Thus, if cor re la tion of malacological data with pol len spec tra at Hrud I is cor rect, it ap pears that some non-cli ma tic fac tors may have in flu enced the pop u la tion of V. diluvianus at that site.

Vari able re la tions be tween Valvata piscinalis and Bithynia tentaculata can be ob served in the neigh bour ing Holsteinian sites at Ortel Królewski and Szymanowo (Szymanek, 2011a) as well as at Boczów in west ern and Zwierzyniec in north-cen - tral Po land (Skompski, 1989); how ever, de tailed stud ies have not been con ducted at those lo cal i ties. A sim i lar pic ture of evo - lu tion of wa ter bod ies is also known at many sites of the Eemian Inter gla cial (Alexandrowicz, 2008; Alexandrowicz and Alexandrowicz, 2010). Usu ally, the as sem blages with V.

piscinalis are con nected with the early stage of the Eemian, whereas B. tentaculata is more abun dant in higher parts of the suc ces sions. In ad di tion fluc tu a tions in con tent of these spe cies ap peared pe ri od i cally dur ing the pre-op ti mal and op ti mal phases of the inter gla cial, as noted for in stance at Piła, Bogdanowo near Poznań or Rogaczewo and Kopaszewko in the vi cin ity of Leszno (Alexandrowicz, 2008; Alexandrowicz and Alexandrowicz, 2010). The as sem blages with V. piscinalis and B. tentaculata are also used in en vi ron men tal re con struc - tions of the Late Gla cial and Early Ho lo cene. V. piscinalis ap - peared ear lier at the end of the Vistulian Gla ci ation and its abun dance of ten points to the main phases of lake de vel op - ment, whereas B. tentaculata be comes more nu mer ous in the Ho lo cene and is typ i cal both of more shal low wa ter bod ies and of zones with rich veg e ta tion, where opercula pre dom i nate in the com mu nity (Alexandrowicz, 1987; W. P. Alexandrowicz, 1999, 2002, 2007).

CONCLUSIONS

The malacofauna at Hrud II dif fers from the as sem blage de - scribed in the vi cin ity of Hrud by Lindner et al. (1991). It sig -

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nif i cantly elab o rates the pic ture of en vi ron ment evo lu tion in this Holsteinian lake, re corded as changes of mol lusc com mu - ni ties. This re flects vari abil ity of hab i tats and palaeo ec ol ogy dur ing the youn ger stage of lake de vel op ment, dur ing a part of the cli ma tic op ti mum. Broader meth ods used for the Hrud I ma - te rial fa cil i tate the in ter pre ta tion. A com bi na tion of the re sults from the east ern and west ern parts of the Hrud palaeolake pro - vides con sid er able malacological data enabling more de tailed en vi ron men tal re con struc tion. The prob lem of the un sta ble

con tent of Lithoglyphus jahni in the de pos its and its palaeo eco - logi cal im pli ca tions re quires fur ther in ves ti ga tion.

Ac knowl edge ments. The pres ent study was fi nan cially sup ported by the sci en tific pro ject BW 1917/3, spon sored by the Fac ulty of Ge ol ogy, Uni ver sity of War saw. I wish to thank to N. Limondin-Lozouet and W. P. Alexandrowicz for many valu able com ments on the manu script. I am ex tremely grate ful to Ł. Giergoń for cor rect ing the Eng lish.

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