The Biostratigraphy, Palaeoecology and Geochemistry of a Long Lacustrine Sequence from NW Greece Dissertation submitted to the University of Cambridge for the degree of Doctor of Philosophy by Michael Reginald Frogley Fitzwilliam College September, 1997 DECLARA TION I hereby declare that this thesis is not substantially the same as any submitted for a degree or diploma or any other qualification at any other University. No part of this work has already been or is being concurrently submitted for any degree, diploma or other qualification. I further state that the text of this dissertation does not exceed 80,000 words. Except where otherwise stated, this dissertation is the result of my own original work and is not the outcome of work done in collaboration. Michae1 R Frogley September, 1997 ABSTRACT Examination of an impOltant new 319m core of lake sediment recovered from Ioannina in NW Greece has attempted to relate changes in the lake to variations in the regional climate of south-central Europe over the last 600,000 years. The site is known to have been extremely sensitive to past climatic change for three reasons: (i) temperate vegetation persisted throughout glacial stages (albeit at low frequencies), so the vegetational response to climatic change would therefore have been almost immediate; (ii) the extreme thickness of the sediments suggests that accumulation rates were high (at times, > 1m per thousand years), which has enabled high-resolution palaeoclimatic reconstructions; and (iii) precipitation of authigenic carbonate has preserved a remarkably sensitive proxy record of productivity variations for most of the lake's history. Well-defined shifts from glacial - interglacial mode have been correlated with vegetational changes identified in a core previously analysed from the same basin (using magnetic susceptibility profiles), enabling tentative correlations to be suggested with other European terrestrial sequences and with the marine oxygen isotope record, back to marine isotope stage 16. Twelve AMS radiocarbon determinations from the upper part of the core, together with the identification of a series of reversed palaeomagnetic events within the Brunhes chron, support the proposed age model for the sequence. The sediments at Ioannina, unlike most of the other long terrestrial European sequences, are calcareous and contain mollusc and ostracod assemblages. Part of this project has involved a comprehensive review of Quaternary and modem aquatic faunas from the lake, as well as the description, illustration and critical assessment of several poorly-known endemic taxa. Faunal assemblage data have been used to provide valuable information concerning the variable response of lake-level to climatic change over time. Convincing new mollusc an evidence indicates low lake-levels at the Last Glacial Maximum, agreeing with regional pollen data, but conflicting with geomorphological evidence derived from Kastritsa, a well-documented nearby Palaeolithic cave site. It is suggested that this discrepancy may be a result of subsequent tectonic uplift of the rockshelter. In addition, stable isotopic analyses of both the ostracods and the bulk carbonate within the sediments have contributed towards deriving a comprehensive palaeoenvironmental history for the site. Although the study analysed physical, biological and geochemical aspects of the entire core, two distinct parts of the record were selected for more detailed investigation. High-resolution analysis over the last interglacial (the Eemian) has revealed evidence for a clear, two-step deglaciation at the beginning of the period, known from elsewhere as the Zeifen-Kattegat Oscillation. Climatic instability has also been detected within the full interglacial. Comparisons are drawn with a range of other Eemian records from across Europe, as well as the Greenland ice cores. High-resolution analysis of the period from the end of the last glacial to the present day has also revealed evidence for climatic instability. A cool and arid oscillation is demonstrated by several climatic proxies that may constitute the first recognition of the Younger Dryas stadial from Greece. A shorter, but more subdued cooling event has also been detected during the first half of the Holocene, which may correspond with a widespread climatic oscillation from high-resolution terrestrial, marine and ice core records that has been dated to between 7,500 and 8,000 years BP. ACKNOWLEDGEMENTS This project would not have been possible without the support, encouragement and enthusiasm of my supervisor, Richard Preece, to whom I extend my most sincere thanks. Over the past four years he has successfully walked a fine supervisorial line, being neither too overbearing nor too inaccessible. His constant stream of ideas, considered criticism and good humour (even down to his continued interest in the molluscan content of the core when a raging field-fire was advancing upon us with alarming rapidity), have provided inspiration even in the darkest moments. On embarking upon this project, I was warned that trying to please two supervisors was probably going to prove the most difficult aspect of all. Thankfully, the tolerance and patience of my second supervisor, Jonathan Holmes, has meant that this has never been a problem. His constant enthusiasm for the project has been matched only by his enthusiasm for e-mail, meaning that despite him being based in Kingston, I have been able to call on his advice with immediate ease. Additional thanks must also go to Chronis Tzedakis, not only for demonstrating the original potential of the loannina sequence and thereby making this project possible, but also for taking on the effective role of an unofficial third supervisor. His infectious wit and good humour have been ably complemented by his constant encouragement, broad knowledge and liking of al fresco lunches. I would also like to take this opportunity to acknowledge the Director of IGME, for making the core material available for study. In particular, the advice of Y. Broussoulis and the assistance given by the loannina staff was invaluable. The multi-disciplinaly nature of this project has meant that expert advice and assistance has been generously provided by a wide range of people and Institutions (although any errors or omissions herein remain entirely my own responsibility). The following deserve special mention (in no particular order): Tim Heaton (NERC Isotope Geosciences Laboratory, Keyworth) for undertaking all the stable isotopic measurements (lightning strikes notwithstanding); Liping Zhou (GIQR, University of Cambridge) for help with the magnetic susceptibility measurements; Barbal'a Maher and team (UEA, Norwich), for providing palaeomagnetic facilities; Huw Griffiths (University of Hull), for patiently helping with the identification of Balkan ostracods and for allowing me to mine his collection of obscure Serbian papers; Tim Atkinson and Peter Rowe (UEA, Norwich), for undeltaking the U-series determinations; Glenn Goodfriend (University of Washington, USA) for undertaking the amino acid analyses (and for providing a stream of cheering anecdotes whilst being stranded overnight in a coach in a Turkish blizzard); Piene and Nicole Lozouet for discussion, hospitality and fine wine whilst examining mollusc an specimens in Paris; Tom Meijer (RGD, Netherlands) for additional molluscan help; Tjeerd van Andel (GIQR, University of Cambridge), for advice, encouragement and for providing a pre-print of his paper on Greek soils; Charles Turner (Open University), for introducing me to the sights and sites of Epirus; Phil Gibbard (GIQR, University of Cambridge) and Jamie Woodward (University of Leeds), for discussion and the retrieval of bedrock samples from Ioannina; James Scourse (University of Wales, Bangor) for support, advice and timely criticism; Mike Hall (GIQR, University of Cambridge), for being persuaded to run several pilot isotopic samples in the Godwin Lab; Geoff Bailey (University of Newcastle Upon Tyne), for access to the Kastritsa samples; Virgin Airways, for providing the means to get the core material back to the UK without bankrupting NERC; Steve Boreham (GIQR, University of Cambridge), for help with the particle-size analyses; Uli von Grafenstein (Technische UniversiUit, Mtinchen), for enthusiasm, encouragement and access to unpublished ostracod isotopic data; David Pyle (GIQR, University of Cambridge), for providing unpublished information on the Morphi tephra; Simon Mansell, for providing floorspace whilst working in the magnetics lab at UEA; and Bill Lee and John Rodford (both Department of Zoology, University of Cambridge), for patient work on the SEM and in scanning and preparing the photographic plates, respectively. Thanks must also go to Ray, Yvonne, Monica and Anne (Museum of Zoology), for providing technical support. The constant encouragement and support of good friends have ensured that my time in Cambridge has been extremely happy. Thanks must go to tolerant lab colleagues Rich Meyrick (for graciously allowing me to dig holes for him in unlikely European locations) and Dave Home (for a great Wallace impression). Special thanks must also go to Rich for being particularly supportive during the bloody, final days of writing-up. Chris Fogwill, Glenn Tattersall and Chris Glaister proved most excellent drinking companions, as did Dave Aldridge, Eleanor Weston and a host of other Zoology reprobates. The loyal Kingston lads also deserve particular· mention, for providing a regular· safe haven for when Cambridge became too much. A NERC Studentship is gratefully acknowledged. Additional financial support was provided by the Department of Zoology and Fitzwilliam College. A Resear·ch Fellowship at St John's College is also gratefully acknowledged, for providing me with the time, facilities and a suitable environment in which to complete this report. CONTENTS 1. INTRODUCTION 1.1 Background 1 1.2 Ioannina 3 1.3 Project Aims 4 1.4 Rationale of this Study 5 1.4.1 The Last Interglacial 5 1.4.2 The Last Glacial - Holocene Transition 5 1.5 Organisation of this Report 6 1.6 Conventions 7 2. PHYSICAL SETTING 2.1 Study Site 9 2.2 Regional Geology 9 2.3 Basin Evolution 13 2.4 Climate 15 2.5 Basin Hydrology 17 2.6 The Modern Lake Basin 18 2.7 Summary 19 3. METHODS 3.1 Introduction 21 3.2 Physical Analyses 21 3.2.1 Core Recovery and Logging 21 3.2.2 Magnetic Susceptibility 22 3.2.3 Palaeomagnetic Analysis 23 3.2.4 Particle-Size Analysis 27 3.2.5 SEM Analysis 28 3.2.6 Modern Faunal Analysis 28 3.2.7 Fossil Faunal Analysis 28 3.3 Chemical Analyses 30 3.3.1 Sediment Geochemistry 30 3.3 .2 Modern Water Chemistry 35 3.3.3 Ostracod Shell Chemistry 36 4. RESULTS 4.1 Physical Analyses 40 4.1.1 Lithological Description 40 4.l.2 Magnetic Susceptibility 42 4.l.3 Particle-Size Analysis 46 4.1.4 SEM Analysis 49 4.2 Chemical Analyses 50 4.2.1 Sediment Geochemistry 50 4.2.2 Modern Water Chemistry 56 4.2.3 Ostracod Shell Chemistry 58 4.3 Summary 63 5. 6. 7. CHRONOLOGY 5.1 Introduction 65 5.2 Correlation with Core 249 65 5.2.1 Basis of the Age Model for 249 66 5.2.2 Correlation of 284 with 249 70 5 .3 Radiocarbon Age Determinations 74 SA Magnetostratigraphy 80 504 .1 Gothenburg excursion 86 504 .2 Mono Lake excursion 86 504 .3 Laschamps excursion 87 50404 Norwegian/Greenland Sea and Fram Strait excursions 87 5.4.5 Blake event 88 504 .6 Jamaica event 89 504 .7 Pringle Falls excursion 90 504 .8 Levantine event 90 504.9 Biwa III excursion 90 504.10 Emperor excursion 92 504.11 Big Lost excursion 92 5.5 Amino Acid Epimerization Data 93 5.6 Uranium-Series Dating 95 5.7 Tephra 97 5.8 Summary and Proposed Age Model 99 FAUNAL BIOSTRATIGRAPHY AND MODERN ASSEMBLAGES 6.1 Introduction 6 .2 Aquatic Molluscan Fauna 6 .2.1 Systematic Review of the Aquatic Molluscan Fauna 6 .2.2 Modern Aquatic Molluscan Fauna 6.2.3 Fossil Aquatic Molluscan Fauna 6.204 Aquatic Molluscan Fauna from Core 256 6 .3 Ostracod Fauna 6.3.1 Taxonomy 6.3 .2 Systematic Review of the Ostracod Fauna 6.3.3 Modern Ostracod Fauna 6.304 Taphonomy 6 .3.5 Fossil Ostracod Fauna: Last Glacial - Holocene 6 .3.6 Fossil Ostracod Fauna: Eemian 6 .3 .7 Other Intervals of 284 604 Summary DISCUSSION 7.1 7 .2 7 .3 704 Introduction Sediment Analyses 7.2 .1 Carbonate Content 7 .2.2 Organic Matter Content 7 .2 .3 Magnetic Susceptibility Faunal Analyses 7.3 .1 Lake-Levels 7.3 .2 The Kastritsa Problem Chemical Analyses 704.1 Modem Waters 704.2 Sediment Isotope Geochemistry 704 .3 Ostracod Shell Chemistry 102 103 108 122 124 126 128 128 129 142 143 145 149 153 154 155 155 156 158 159 161 161 162 164 164 165 169 7.4.4 Open or Closed Lake System? 7 .5 Synthesis 7.5.1 Eemian 7.5.2 MIS-5d - Last Glacial Maximum 7.5.3 Last Glacial - Holocene Transition 7.5.4 Response Times 7.6 Summary 8. COMPARISON OF 284 WITH OTHER LONG RECORDS 9. 8.1 8.2 8.3 8.4 8.5 8.6 Introduction TelTestrial Sequences Marine Record Ice Cores Rapid Climate Fluctuations 8.5.1 The Eemian 8.5.2 The Montaigu Event 8.5.3 The Last Glacial 8.5.4 The Last Glacial- Holocene Transition Summary CONCLUSIONS REFERENCES PLA TES I - VII APPENDICES Appendix A: Appendix B: Appendix C: Modern Water Chemistry Data Sampling Site Details Eemian Pollen Diagram from Core 284 172 175 176 180 180 186 187 190 190 194 195 197 197 200 201 202 203 205 209 1. INTRODUCTION 1.1 BACKGROUND Interest in past climatic change has acquired an important profile in recent years. We have gradually become aware through issues such as global warming that human impact upon the environment can have far ranging consequences. By gaining clearer insights into the mechanisms that drove ancient climatic systems we can hopefully achieve a greater understanding of how the current climate operates and might then apply such understanding in the prediction of future climatic change. The study of the Quaternary is a multidisciplinary endeavour largely concerned with piecing together the evidence for ancient climatic change that has become preserved in oceanic, continental and ice core sequences. Traditionally, the 'yardstick' for the Quaternary has been the long continuous record of the deep oceans, where huge thicknesses of sediment have accumulated, largely undisturbed by the periodic glaciations that have rendered much of the continental sedimentary record highly disjointed and fragmentary. Over the last thirty years or so, an effective mm·me chronology has been established (the mm·ine oxygen isotope record) that details palaeoclimatic variability throughout the Quaternary (and much em·lier periods). Recently however, attention has refocused on continental sequences, especially those that have accumulated in lake basins beyond the reach of the ice sheets, such as those in southern Europe. Under favourable geological conditions, a limited number of thick sedimentm), sequences have accumulated at far faster rates than those operating in the oceans, so preserving the palaeoclimatic record in much greater detail (fig. 1.1). In addition, these lacustrine sequences cover much longer periods of time than most of the fragmentm), continental records from northern Europe. One of the fundamental challenges now facing Quaternary researchers is the detailed analyses of these long, continuous sequences. The new core that forms the focus of this study is from Ioannina, a lake basin in northwestern Greece. It represents one of these rare, continuous continental southern European records and is unusual in terms of its climatic sensitivity as well as its physical and strati graphical length. 1 1 La Grande Pile 2 Les Echets 3 Lac du Bouchet / Prac1aux 4 Padul 5 Valle di Castiglione 6 Monticchio 7 Ioannina 8 Tenaghi Philippon -' Fig. 1.1 Location map of principal long European terrestrial sequences. S2 ;;5 o tl c:: Cl :::l o =<: • N INTRODUCTION • 3 1.2 IOANNINA Previous work on the Quaternary of the loannina region has been rather sparse. The first detailed research was conducted in the 1960s by the archaeologist Eric Higgs and his co-workers, who largely concentrated their efforts on the Palaeolithic site of Kastritsa in the south of the basin (e.g. Higgs and Vita-Finzi, 1966; Higgs et al ., 1967). It was Bottema (1974) who first demonstrated the potential of the loannina sequence. He analysed pollen from two short cores located in the northern prut of the basin and showed that they extended back to the last glacial. More recently, the area has been extensively cored by the Greek Institute of Geology and Mineral Exploration (IGME), who have been investigating the lignite potential of this and adjacent basins. They originally drilled almost 300 individual boreholes of varying length, although many have since been discarded. From the surviving archived material, Tzedakis (1991, 1993, 1994) selected and analysed the pollen record from a long core taken from the south of the basin (no. 249, 185m in length, unbottomed) . It covered a series of glacial - interglacial cycles during the last 430ka which enabled cOlTelation with other European continental sequences and the mru'ine oxygen isotope record. In addition, he demonstrated that the continued presence of temperate ru'boreal taxa at loannina even during glacial stages, albeit at low frequencies, identified the site as a long-term refugial area (e.g. Bennett et aI., 1991; Tzedakis, 1991 , 1993). This is cleru'ly extremely important, since the continued presence of temperate taxa not only ensures a rapid response to climatic wruming at the beginning of an interglacial (minimising migration lags which ru'e seen elsewhere), but also confirms the extreme sensitivity of the region to climatic variability. This work further highlighted the enormous potential of the loannina record and paved the way for this new project. The original intention had been to analyse other climatic proxy indicators at high­ resolution from core 249 and compare them with the response of the vegetation record. Unfortunately, it transpired that the original core material had been inadvertantly discarded since the sub-sampling for the palynological investigation of 249 (Tzedakis, 1991). Attention was therefore focused on two alternative long IGMB cores taken in close proximity to 249. These were made available for study and returned to Cambridge in 1993. The longest, core 284, was located less than half a kilometre to the southwest of 249 and at 319m unbottomed length, was over lOOm deeper and therefore likely to have a longer stratigraphical range. Core 284 appears to have formed continuously in a part of INTRODUCTION • 4 the basin that was, until recently, always submerged. Core 256, located approximately 6km to the southwest of 284, reached bedrock at 130m. It is thought to represent a more marginal environment, a conclusion based on its geographical location, the nature of its lithologies and the presence of a series of hiatuses within the record. Preliminary palaeontological and palaeomagnetic work has shown that it covers a longer time-span than 284 (the bottom 60m is palaeomagnetically reversed). However, because of the gaps in the record, there is uncertainty over its exact chronology. It is therefore considered unsuitable for additional detailed analysis and will not be considered further. As a result, the work presented in this report is entirely based on the detailed analysis of core 284. 1.3 PROJECT AIMS The principal aims of this study can be summarised as follows: • To establish a robust chronology for the entire sequence that can be verified by independent means. • To reconstruct the palaeoclimatic history of the Ioannina region by means of high­ resolution, multi-proxy analyses that complement and can be correlated with the exisiting pollen stratigraphy from the adjacent 249 sequence. • To investigate the evidence for high frequency climatic variability through selected parts of the record. • To use the high-resolution data as a means of assessing the variable response times ('leads and lags') between pollen and other proxies to climatic change. • To undertake a comprehensive study of the modern and fossil mollusc an and ostracod faunas in order to assess the possibility of using faunal changes as biostratigraphical markers and to provide detailed palaeoecological information on lake history. • To assess the importance of the sequence in relation to other long European terrestrial records, the marine record and the ice cores and to suggest correlations where appropriate. • To assess the potential for future work on the sequence. INTRODUCTION. 5 1.4 RATIONALE OF THIS STUDY The extreme physical length of a sequence such as Ioannina 284 presents celtain logistical problems with regard to formulating an efficient programme of study. The approach taken in this case was to apply a series of analyses to the entire sequence, in order to characterise the overall stmcture of the sequence and to help derive a chronological framework. Two selected parts of particular interest were then chosen for high-resolution investigation. These were the last interglacial (the Eemian) and the last glacial - Holocene transition. 1.4.1 The Last Interglacial Known as the Eemian in the northwest European continental record, and marine oxygen isotope stage (MIS) 5e in the oceanic record, the last interglacial began about 130,000 years ago and lasted approximately 10 - 13,000 years (e.g. Imbrie et al. , 1984). Until recently, it has been considered a relatively stable, warm period, with temperatures only slightly higher than at present. However, recent high-resolution isotopic evidence from the Greenland Ice-core Project (GRIP) has suggested that this period was in fact punctuated by a series of high frequency climatic oscillations (GRIP members, 1993) . This suggestion has prompted much scientific debate (e.g. Grootes et al., 1993; Bender et al., 1994; 10hnsen et al., 1995), particularly as another Greenland ice core (GISP2), located less than 30krn to the west of the GRIP site, has failed to corroborate evidence for these oscillations. Researchers have so far been unable to confirm unambiguously the existence of these climatic fluctuations in either marine or continental sequences. One of the fundamental aims of this project is therefore to examine the last interglacial at Ioannina for evidence of rapid climatic oscillations. 1.4.2 The Last Glacial - Holocene Transition Following the height of the last glacial (the 'Last Glacial Maximum', about 20ka BP), the Earth's climate steadily warmed until about 11ka BP, when there. was a short-lived but intense cooling event, known as the Younger Dryas (YD). This lasted for about 1,000 years, during which temperatures returned to almost full glacial values. At about lOka BP, global temperatures subsequently climbed steadily and rapidly, and the Earth's climate entered the current interglacial (the Holocene). Although conditions have remained relatively stable during this time, several rapid climatic oscillations have INTRODUCTION • 6 been recorded, in particular a brief cooling event during the first half of the Holocene (about 7.5-8ka BP) that may be global in exent (e.g. Alley et al., 1997). The YD was originally thought to be solely a North Atlantic phenomenon, but subsequent records from elsewhere (e.g. nOlthern Europe, Greenland, the Pacific, Asia, North and South America) have established that it was global in extent (Frakes et al., 1992). According to Willis's (1995) review of Balkan vegetational history, no clear and unequivocal YD signal has yet been detected from Greek pollen records, which she explains might be due to elevational factors. Although the pollen record from core 249 did not reveal the presence of the YD (probably because the uppermost Palt of the record was missing), Tzedakis (1993) noted that the Ioannina site appeared to be palticularly sensitive to climatic change (the reasons for which have been outlined above). A brief intra-Holocene cooling event at around 7.5ka BP has previously been recorded in Greek pollen sequences and linked to the abmpt disappeal'ance of Pistacia from the vegetational record (e.g. Rossignol-Strick, 1995). This project will therefore attempt to establish the existence of both the YD and evidence for intra-Holocene climatic instability in the Ioannina record. Additionally, an assessment of the timing and nature of any anthropogenic (i.e. human) disturbance in the region will be attempted. 1.5 ORGANISATION OF THIS REPORT This report is arranged into chapters as follows: • Chapter 2 Introduces the study site and presents details of its physical setting with regal'd to regional geology, basin evolution, climate and hydrological factors. The chapter concludes by considering aspects of the modern lake basin. • Chapter 3 Presents detailed accounts of the physical, chemical and faunal analytical methods employed during this project. • Chapter 4 Presents the results from the chemical and physical analyses of the sediments. • Chapter 5 Outlines the different methods by which a chronological framework has been derived for the sequence and concludes by presenting a detailed age model that is used throughout the rest of the study. • Chapter 6 Provides details of the modern and fossil molluscan and ostracod faunal analyses. Previous faunal work is reviewed and updated. The importance INTRODUCTION • 7 and potential of the fauna for biostratigraphical and palaeoenvironmental purposes is assessed. • Chapter 7 Discusses and interprets the results with particular reference to the way in which lake systems operate. A synthesis of all results is then presented in order to derive a comprehensive palaeoenvironmental history of the lake basin. • Chapter 8 The Ioannina sequence is assessed in relation to other long terrestrial, marine and ice core records. Potential correlations are suggested where appropriate. • Chapter 9 Draws together the main conclusions of the project and suggests possible avenues for future research. 1.6 CONVENTIONS Since there is no detailed and widely accepted stratigraphical scheme for southern Europe, reference is occasionally made to the local scheme proposed by Tzedakis (1991) from the Ioannina 249 sequence, although this is highlighted wherever appropriate. Although not applicable in the strictest stratigraphical sense, the last interglacial is referred to throughout as the Eemian. This convention is for the sake of convenience, reflecting the broad, informal use that the name currently enjoys throughout the literature. The terms 'glacial' (or 'cold stage') and 'interglacial' (or 'warm stage') are often used informally to denote periods of relatively cold or warm (temperate) climatic conditions, respectively. Radiocarbon dates or ages are quoted as uncalibrated years before 1950 AD (BP). Otherwise, dates or ages are given as years ago, where the abbreviations Ma and ka are used to represent millions and thousand of years ago, respectively. Other abbreviations in the text are explained in full at their first usage: examples include Younger Dryas (YD); Last Glacial Maximum (LGM); marine isotope stage (MIS); Zeifen-Kattegat Oscillation (ZKO); and dissolved inorganic carbon (DIe). Greek symbols used to denote certain quantities or parameters (for example, the standard delta notation for representing isotopic ratios) are explained at their first usage. Geographical place names present celtain problems, in that there usually exist several possible translations from Greek into English (for example, Ioannina is often referred to as Janina, Jannina or Yannina). Throughout this report therefore, one spelling is used consistently throughout. Where appropriate, Yugoslavia is taken to consist of Serbia and Montenegro. INTRODUCTION • 8 The extended character set used in the production of this report does not permit the use of certain accented letters that are common in the Serbian and Croatian languages (for example, an's' or a 'c' beneath an inverted caret 1\ symbol). In such cases, the un­ accented English equivalent is given throughout (including the references). 2. PHYSICAL SETTING 2.1 STUDY SITE Lake Pamvotis (470m above sea-level) is situated in the Ioannina basin within the region of Epirus in north-western Greece. The site is situated on the western flank of the Pindus Mountain Range, approximately 60km from the Ionian coast (fig. 2.1). The basin extends from Protopappa in the north-west to Ampelia in the south. It is approximately 30km in length and approximately 15km at its maximum width. During the late 1980s, the Institute of Geology and Mineral Exploration (IGME) investigated the Ioannina basin for commercially exploitable lignite deposits. Other basins in the Pindus had previously yielded economically viable deposits and the Ioannina basin was also considered worthy of detailed investigation. Almost three hundred cores were eventually drilled across the basin. Unpublished reports by IGME record the presence of several thin, discontinuous lignite beds that have been broken up by the sub-basin tectonics (see below). They are currently not considered worthy of of commercial exploitation becauseftheir depth and severely limited thickness. The core that forms the focus of this study is number 284 (39°45'N 20°51 'E, 472.69m above sea-level). It was selected on the basis of several criteria that included continuity, condition, overall length and proximity to core 249 (section 1.2). At 319m total length, core 284 is one of the longest cores recovered from the Ioannina basin, but despite this it still does not reach bedrock; drilling was ceased when it became obvious that no lignites were likely to be encountered. Subsequent IGME stratigraphical reports (unpublished) show that the core had been drilled in one of the deepest sub-basins, making it an ideal candidate for this particular study. Located less than a kilometre from core 249, it also appeared to be free from obvious lithological breaks and had been preserved in a reasonable condition. It is described in considerably more detail in section 4.1.1. 2.2 REGIONAL GEOLOGY The Ioannina basin is a synclinal structure that was formed during tectonic movement in the Ionian isopic zone, prut of the broad external zone of the Hellenides (Aubouin, 2. PHYSICAL SETTING 2.1 STUDY SITE Lake Pamvotis (470m above sea-level) is situated in the Ioannina basin within the region of Epirus in north-western Greece. The site is situated on the western flank of the Pindus Mountain Range, approximately 60km from the Ionian coast (fig. 2.1). The basin extends from Protopappa in the north-west to Arnpelia in the south. It is approximately 30km in length and approximately 15km at its maximum width. During the late 1980s, the Institute of Geology and Mineral Exploration (IGME) investigated the Ioannina basin for commercially exploitable lignite deposits. Other basins in the Pindus had previously yielded economically viable deposits and the Ioannina basin was also considered worthy of detailed investigation. Almost three hundred cores were eventually drilled across the basin. Unpublished reports by IGME record the presence of several thin, discontinuous lignite beds that have been broken up by the sub-basin tectonics (see below). They are cUlTently not considered worthy of of' commercial exploitation becauseftheir depth and severely limited thickness. The core that forms the focus of this study is number 284 (39°45'N 20°51 'E, 472.69m above sea-level). It was selected on the basis of several criteria that included continuity, condition, overall length and proximity to core 249 (section 1.2). At 319m total length, core 284 is one of the longest cores recovered from the Ioannina basin, but despite this it still does not reach bedrock; drilling was ceased when it became obvious that no lignites were likely to be encountered. Subsequent IGME stratigraphical reports (unpublished) show that the core had been drilled in one of the deepest sub-basins, making it an ideal candidate for this particular study. Located less than a kilometre from core 249, it also appeared to be free from obvious litho logical breaks and had been preserved in a reasonable condition. It is described in considerably more detail in section 4.1.1. 2.2 REGIONAL GEOLOGY The Ioannina basin is a sync1inal structure that was fOlmed during tectonic movement in the Ionian isopic zone, part of the broad external zone of the Hellenides (Aubouin, Kato Lapsista Extent of lacustrine deposits in basin o Skm PHYSICAL SETTING • 10 N I Fig. 2.1 Location maps illustrating critical places and core sites referred to in the text. N t o ke PHYSICAL SE1TING • 11 Skm + 284 Core Location Alluvial Fans Quaternary Deposits Flysch Palaeogene Limestone Upper Senonian Limestone Vigla Limestone Posidonia Beds Pantokrator Limestone Fig. 2.2 Summary geological map of Ioannina basin (after IGSR-IGP, 1966 and Perrier et al. , 1967). Inset shows isopic zones of Hellenides (after Aubouin, 1959). PHYSICAL SEITING • 12 1959). These zones are generally thrust-bound and composed of similar facies (fig. 2.2). Mesozoic carbonates were defOlmed during a period of thmsting known informally as the Hellenide contractional event (related to the Alpine Orogeny further west) during the mid-Eocene - Oligocene. A westward-migrating thrust sheet overrode the Gavrovo zone to the east on the Pindus Thmst and folded the Ionian zone into a series of north north-east trending anticlines and synclines (Clews, 1989). The result was the fOlmation of the Pindus Mountains and an associated foreland thmst basin to the west. During the Oligocene - Lower Miocene, erosion of the newly formed Pindus resulted in a rapid influx of clastic sediments into the foreland basin, intermpting the carbonate sedimentation that had dominated since the early Mesozoic. These ranged from coarse, quartz-rich clastics in the east to mads in the west. The sediments have been interpreted largely as submarine fan deposits, with palaeocurrent data suggesting input from the east (Piper et al., 1978). Upper fan and basin slope deposits dominate in the east (Gavrovo zone), whilst further west, more distal turbidite sequences of shales, silts and current-rippled sands dominate (Ionian and Pre-Apulian zones). It seems likely that the flysch deposits currently outcropping in the east of the Ioannina basin (mostly silts, sands and medium- to fine-grained conglomerates) represent a mid-fan environment. Inner arc extension trending N-S behind the Hellenic Arc to the south (associated with subduction) in the Late Pliocene allowed a series of WNW and ENE non-marine basins to open (Clews, 1989). Transfer zones (consisting of NNW and NE tt·ending faults) that linked the basins enabled them to elongate. During the Early Pleistocene, compressional tectonics became dominant in Epims due to the continued collision of the Greek (Anatolian-Aegean) block with the Apulian continental block to the north and west (e .g. Clews, 1989; King et al., 1993; Jackson, 1994; King et al., 1994; Le Pichon et al., 1997). This regime is still active today, as demonstrated by the rejuvenated profiles of rivers such as the Thiamis and Louros (King and Bailey, 1985), as well as evidence of uplift from the Ioannina basin itself (discussed below). The Pindos experienced localised glaciation during the Quaternary, although clear geomorphological evidence only exists for the last glacial period (e.g. Denton and Hughes, 1981; Lewin et al., 1991). Even so, little research has been carried out as to the extent and number of localised glacial events and more fieldwork and detailed mapping are necessary (Tzedakis, 1991). The main lithological units seen outcropping in the Ioannina basin are detailed below. Their distribution is illustrated in fig. 2.2 (after IGSR-IGP, 1966; Perrier et al., 1967). PHYSICAL SETTING • 13 Pantokrator Limestone (Lower Jurassic). White, maSSIve onchoidal limestone, containing algal remains and brachiopods from the Lower - Middle Lias, mostly outcropping in the north-western part of the basin. Posidonia Schists (Upper Jurassic). Thinly bedded silica-rich argillaceous deposits containing abundant radiolaria and bivalves. They outcrop to the north-western part of the basin. Vigla Limestone (Upper Jurassic - Lower Cretaceous). Well-bedded pinky-cream limestone with flint nodules, seen across the basin. Upper Senonian Limestone. White, well-bedded limestone containing rudist (reef­ building bivalve) fragments and flint nodules. Dominates the periphery of the basin. Palaeogene Limestone. Yellow-white, massive limestones outcropping to the south­ east of the basin, displaying minor karst development. Tertiary Flysch (Upper Eocene-Lower Miocene). Marlstones, siltstones, sandstones and intercalated fine-grained conglomerates outcropping to the eastern part of the basin. Quatemary deposits. Alluvial and lacustrine sediments (mostly clays and silts) present across the main floor of the basin. These are discussed in detail below. 2.3 BASIN EVOLUTION Karst solution- of the Ioannina syncline carbonates and continual movement along the boundary faults fOlmed the original basin or polje. IGME suggest that in Late Pliocene / Early Pleistocene times, the basin floor was sealed by braided river deposits which allowed the formation of the lake. Cores show fluvial sediments that give way rapidly to lacustrine deposits; this lithological succession has been designated the Anatoli FOlmation (Broussoulis et al., in prep.). Consisting of silts, clays, calcareous gyttja and two main lignite bands, these lacustrine deposits can be found in cores stretching from Kato Lapsista in the north to Ampelia in the south. IGME have attributed a Lower Pleistocene age to these deposits by comparing pollen data from core 123 (taken from the northern prut of the basin) with similar palynological studies from elsewhere in Greece (e.g. Benda et al., 1987). Current lack of any independent chronological control for the Ioannina pollen data however, means that any dating must remain questionable. A depositional hiatus is overlain by beds of the Kastritsa Formation, a conformable sequence of sands, silts, clays, calcru'eous gyttja and another two lignite bands (Broussoulis et al., in prep.). These deposits are found in cores taken from two separate areas of the basin: around Kato Lapsista in the north; and around the present- PHYSICAL SE1TING • 14 day lake, stretching from south of Katsikas, Kastritsa and Loghades, to Perama in the north. The geometry of the sand deposits has been interpreted as indicative of alluvial fans bringing eroded flysch material in from the east. These fans are present south of the Anatoli - Loghades line. As mentioned above, apart from some tentative pollen comparisons, IGME have only stratigraphic evidence to justify their attribution of the Kastritsa Formation to the Middle and Upper Pleistocene. By studying the lignite stratigraphy of the whole basin, IGME have suggested that several sub-basins developed, each of which was susceptible to variable and independent tectonic subsidence. The sub-basin in which core 284 was drilled is considered to have been the deepest (Y. Broussoulis, pers comm.). In addition, the dominantly silt lithologies of 284 (see section 4.1.1) suggest that it was drilled through the Kastritsa Formation, beyond the furthest extent of the alluvial fans. It is interesting to note at this point that a scheme to classify Mediterranean valley sediment sequences was first proposed by Vita-Finzi (1969). He suggested that phases of alluviation throughout the Mediterranean region were climatically controlled and resulted in two main sedimentary units: the 'Older Fill', characterised in Epims by the red beds of the Kokkinopilos Formation; and the 'Younger Fill', characterised in Epirus by the drabber Valley Floor Alluvium. This overly simple classification has since been widely questioned, as regional alluvial stratigraphies are often much more complex than this two-fold system might suggest (e.g. Butzer, 1980; Wagstaff, 1981; Pope and van Andel, 1984; Gomez, 1987; Harvey and Wells, 1987; Lewin et al., 1991; van Andel, in press). These doubts are ably supported at Ioannina by the complex alluvial history detailed above. Accordingly, no further use of any of these terms will be made during this study, however an interesting review of the development of the OlderIYounger Fill story is given by Grove (1997). The soils developed on the catchment geology will be an imp0l1ant component of any alluvial deposit. According to the somewhat confusing study made by MacLeod and Vita-Finzi (1982) on the soils and alluvial deposits of Epirus, they broadly fall into two main categories: terra rossa red beds and so-called brown Mediterranean soils. However, a detailed study on the palaeosols and red beds of Greece (van Andel, in press) points out that terra rossa sensu stricto is now a relatively rare in situ deposit in the region. True terra rossa is developed on karstic limestone terrain as a direct result of dissolution, its strikingly characteristic red colouration being derived chiefly from the iron-rich insoluble residue. Most terra rossa seen in the region is therefore a secondary, redeposited sediment. It typically has a bimodal composition, with up to 30% consisting of silt-sized quartz material and around 70% consisting mainly of clay-sized PHYSICAL SETTING. 15 material. The mineralogy of this fine fraction is dominated by kaolinite, illite and to a lesser extent, smectite (van Andel, in press). The clay fraction is derived from dissolution of the limestone (the colour resulting from abundant iron oxides in the residue, mostly haematite and goethite), whereas the silt fraction is thought to be derived from aeolian material, brought by scirocco winds from the deserts of north Africa (MacLeod, 1980). Brown Mediterranean soils, on the other hand, develop on both flysch areas and the chert and shale bands associated with some of the limestones. Both of these lithologies are present in the basin, the flysch outcropping extensively to the east and the Posidonia beds outcropping in a limited area to the north-west. MacLeod and Vita-Finzi (1982) note that these soils typically have a higher fine-sand component than the red beds (-50% as opposed to -10%). Their clay-sized component, whilst generally lower than the red beds (-25 % as opposed to -70%), is characterised by relatively high proportions of the clay minerals illite and montmorillonite. The iron hydroxide mineral goethite (often derived originally from haematite) is thought to be primarily responsible for imparting the drab brown colour to the soil. For a comprehensive discussion of the palaeosols and red beds of the region, see van Andel (in press). Fans consisting of a broad range of alluvial material can mainly be seen along the northern margin of the present day basin (at the base of the Mitsikeli ridge), as well as just north of -Arnpelia (fig. 2.3) . Other geomorphological features of note are the terraces that can be seen occasionally around the margins of the basin, for example those mapped to the far east, south of Loghades (IGRS-IFP, 1966). Higgs and Vita­ Finzi (1966) also record several terraces that they interpret as raised beaches located to the west of the airport (north-west of the lake), the lowest of which is 12m above the current lake-level. IGRS-IFP (1966) however, map these deposits as the remains of ancient siliceous alluvial fans, rather than raised beaches. Similar fan deposits are also recorded in the far south of the basin, east of Ampelia. The possibility of tectonic movements within the basin are discussed in section 7.3.2. 2.4 CLIMATE The Mediterranean experiences a complex transitional climate, since it is effectively sandwiched between temperate maritime, temperate continental and arid subtropical desert regions. The climatic system is largely controlled by the westerlies in winter and the subtropical anticyclone in summer (Barry and Chorley, 1992). This results in the PHYSICAL SETTING • 16 characteristic hot, dry summers and the mild, wet and windy winters associated with a typical 'Mediten'anean climate'. It should be noted that the actual definition of a 'Mediterranean climate' is not easy. Different climate classification schemes invariably invoke different criteria, reflecting the complexity and limited understanding of the current climatic system. For example, much of the Meditenanean falls into the Cs category of the classic Koppen scheme, which requires rainfall in the wettest winter month to be at least three times that of the driest summer month (Wigley and Farmer, 1982). Aschmann's (1973) definition is much narrower however, specifying a range of annual precipitation (between 275-900mm), a mean winter temperature below 15°C and the hours per year at which the temperature is below freezing to be no more than 3% of the total. A detailed discussion is beyond the scope of this report, but both Wigley and Farmer (1982) and Barry and Chorley (1992) provide comprehensive reviews. A brief summary is given below. Following a long and generally unpredictable spring (March - May), collapse of the Eurasian high-pressure cell is accompanied by northern and eastwards expansion of the Azores anticyclone from the west. This results in a northwards movement of depressions into continental Europe, markedly reducing the chances of precipitation. By mid-June, the expanding Azores anticyclone becomes the dominant factor controlling the weather (Barry and Chorley, 1992). A low-pressure trough that develops across northern Africa ensures that most of the winds are from the north (e.g. the etesians of the Aegean), derived from an extension of the north-east trades. Regional winds are also important, such as the hot, dry and dusty airstreams of tropical continental origin blowing northwards (e.g. the sciroccos). Precipitation is generally low and many meteorological stations record very little or no rain for at least one of the summer months. Towards the end of October, the onset of winter is usually heralded by the swift collapse of the Azores anticyclone (Barry and Chorley, 1992). Air masses from the north-west also invade frequently, derived from a southerly-displaced branch of the Polar Front Jet Stream. These push the Atlantic and Genoa-type depressions (the latter forming in the lee of the Pyrenees and Alps) to the east. Incoming winds from north Africa and Asia mean that the movement of these depressions is often complex, particularly in the eastern Meditenanean (Wigley and Farmer, 1982). Convective instability is ensured by a combination of relatively warm sea-surface temperatures and cool air temperatures (up to 2°C difference during January), meaning that intense precipitation often results (Barry and Chorley, 1992). PHYSICAL SETTING. 17 Orographic effects (the topographical 'blocking' of weather fronts) are extremely important local factors throughout the Mediterranean region that are capable of producing small-scale but generally sharp contrasts in precipitation (Wigley and Farmer, 1982). For example, the Pindos Mountains in Epirus are oriented parallel and in close proximity to the Ionian coast and perpendicular to the easterly-tracking winter depressions. This has a marked orographic effect, causing high precipitation over the region and an effective rain-shadow further to the east. A marked moisture gradient therefore exists west - east over northern mainland Greece. As a west-facing site at -470m above sea-level in the western reaches of the Pindos, Ioannina falls well within the zone of high precipitation referred to above (it is one of the wettest mainland meteorological stations in Greece). Annual precipitation is 1204mm, with December the wettest month (176mm) and August the driest (29mm). The high Pindos ensure that Ioannina receives a degree of shelter from cold north­ westerly winds (derived from the Polar Front Jet Stream) during winter months, meaning that the average January temperature is around 5°C. Lake Pamvotis therefore freezes only a few times per century (Tzedakis, 1991). During the summer, mean temperatures reach -25°C, although during the period 1951-1980 the maximum recorded temperature was 41°C, in 1973 (all data from Tzedakis [1991], originally derived from records of the National Statistical Service of Greece). In experiencing warm, dry summers and cold, wet winters therefore, the climate of Ioannina can be broadly described as 'Mediterranean' with a degree of continentality, to account for its elevation and distance from the coast (Tzedakis, 1991). 2.5 BASIN HYDROLOGY No detailed studies on the hydrology of the lake basin have been published, but a few overviews do exist, the main points from which are summarised here. The lake can be broadly classified as an effectively closed hydrological system, since it has no outflowing streams or major basin drainage. This is a crucial factor, since closed lake basins have been shown to display lake-level changes that are largely a response to climatic changes in precipitation and evaporation. Anagnostidis and Economou-Arnilli (1980) summarise some of the main hydrological features of the modern basin. They highlight the fact that the lake forms the base-level of thekarst aquifer underlying the Mitsikeli ridge (altitude: 1,81Om), which is drained by the springs that feed the lake on the nOlthern and eastern shores. Two of the main ones are located on the shore just north of the island of Nissi and near the settlement of Goritsa to the north-west. There PHYSICAL SEITING • 18 is no permanent outflow, although it is thought that blocked sink-holes (or katavothrae) present in the floor of the lake occasionally become unblocked for a short time (e.g. Fels, 1957; Higgs et al., 1967). It may therefore be difficult to distinguish climatically­ driven lake-level variation from that caused by, for example, earthquake activity temporarily unblocking the sink-holes. Runoff from the mountains to the east is minimal, since surface waters disappear into karstic sink-holes and reappear through the springs (Conispolatis et al., 1986). However, run-off from the lowland plain to the north-west is more substantial (Anagnostidis and Economou-Amilli, 1980). The modern water chemistry of the lake is discussed in detail in section 4.2.2. In summary, it can be considered as a typical freshwater temperate hard-water lake, slightly alkaline (pH = -7.6) and dominated by Ca2+ and HC03· ions. The thermoc1ine is not very pronounced (Overbeck, 1980). Some of the main hydrological parameters of the catchment are summarised in table 2.1. Total mean annual precipitation Evapotranspiration Infiltration Runoff Annual yield of springs 1236mm per yr 545mm per yr 495mm per yr 196mm per yr 45 x 106m3 per yr Table 2.1 Water budget for total sUlface of catchment area of Lake Pamvotis . Data taken from Marinos (1974) and Anagnostidis and Economou-Amilli (1980) . 2.6 THE MODERN LAKE BASIN The city of Ioannina, with a population of approximately 100,000 inhabitants, is situated on the western shore of Lake Pamvotis. The agricultural area of the basin (approximately 133,000 acres) is mostly planted with corn, tobacco and vegetables (Albanis et al., 1986). The lake itself is eutrophic, with abundant phytoplankton in the surface waters thriving from the pollutants introduced from various sources (human and industrial waste, agricultural pesticides). Falling fish stocks and the constant presence of unpleasant dark green algal blooms mean that pollution of the lake is becoming a serious ecological concern (e.g. Albanis et al., 1986; Kalogeropoulos et al. , 1994). PHYSICAL SETTING. 19 The modern lake cunently has a maximum depth of around lOm and an areal extent of 22.8km2• It is approximately 8km in length (along its longest axis) and has a maximum width of approximately 5km. Throughout historical times, the lake was more extensive than it is today. At the end of the nineteenth century, part of the lake and the marsh around Lampsista to the north were attificially drained for agricultural purposes. Completed in 1944 (Fels, 1957), this was achieved via a 17km long canal linking to a 4km long tunnel constlUcted through the Tomarokhoria Plateau in the west, emptying into the Kalamas River. The 10MB boreholes were therefore all drilled on dry land. There is little surrounding natural vegetation remaining in the basin due to cultivation, logging and over-grazing of the land by domestic animals. These activities have also largely contributed to the destabilisation and erosion of the soils. Around the lake itself, the vegetation consists lat°gely of the free-standing reeds Phragmites communis, along with Potamogeton peifoliatus, Typha augustifolia, Scirpus holoschoenus, S. lacustris, Cyperus longus, and Sparganium erectum amongst others (Higgs, et al., 1967; Bottema, 1974). Sparse open-canopy blUshwoods and low thickets (dominated by the evergreen oak, Quercus coccifera) at°e the main vegetation types on the lower uncultivated slopes and alluvial fans below about 1,OOOm (Higgs et al., 1967). Other taxa, such as Juniperus oxycedrus, Pistacia terebinthus, Ostrya carpinifolia and several other kinds of thorny shlUb also occur. Above this level and up to the tree-line (approximately 1,700m), remnants of a mixed forest can be determined, composed chiefly of Fagus sylvatica, Pinus nigra, Abies cephalonica and in the upper reaches, Juniperus communis (Higgs et al., 1967). It has been suggested (Higgs et al., 1967; Bottema, 1974) that in the absence of human activity, the natural vegetation of the basin would be a deciduous forest dominated by Quercus coccifera up to about 1000m. Above this level, a mixed beech-pine-fir forest would dominate, with the possibility of some sub-alpine taxa (such as Daphne oleoides) at the highest elevations. 2.7 SUMMARY This chapter described the physical setting of the study site, by first considering the regional geology of EpilUs and then by outlining the detailed evolution of the lake basin itself. Tectonic movements during the mid-Eocene to Oligocene deformed the extensive Mesozoic cat°bonates of the region and folded them into a series of anticlines and synclines. The newly formed Pindos Mountains provided substantial quantities of clastic material to the region, which were deposited as a series of turbidite fans into the foreland thrust basin that had developed to the west of the new mountains. Extensional PHYSICAL SETTING • 20 deformation in the Late Pliocene encouraged a series of elongated non-marine basins to form, followed by a return to a compressional tectonic regime during the Early Pleistocene. The region was probably subject to localised glaciation throughout all glacial phases of the Quaternary. The Ioannina basin itself developed on a syncline. Solution of the limestone basement created a depression known as a polJe which, coupled with tectonic subsidence along the boundary faults, led to the development of the lake basin. Extensive coring by IGME revealed that the floor of the basin was sealed, probably in Plio-Pleistocene times, by braided river deposits that were quickly succeeded by lacustrine sediments. Evidence from lignite bands suggests that several sub-basins developed, each of which was subject to a variable tectonic history. It seems likely that the basin through which core 284 was drilled was the deepest of these sub-basins . The geomorphology of the current basin was also discussed, along with evidence for previous lake levels. The climate of the region was then considered. Ioannina is subject to a 'Mediterranean' type climate, in that it experiences cold, wet and windy winters, along with watm and dry summers. The elevation of the site and its distance from the coast are also important, as they impatt a degree of continentality to the climatic regime. The orographic effect of the Pindos ensures high levels of precipitation from easterly­ tracking depressions during winter months, yet also shelter the region from the coldest north-westerly winds derived from the Polar Front Jet Stream. The little information that exists on the hydrology of the basin was reviewed. The lake forms the base-level of a karstic aquifer, much of which is present under the Mitsikeli Ridge. A typical temperate hat'd-water lake, it receives water both from Mitsikeli, via a series of springs on the northern and eastern shores, and runoff from the plain to the north-west. As there is no permanent outflow, the lake can be considered an effectively closed system, although a series of underground sink-holes (known as katavothrae) may become intermittently unblocked and allow the lake to drain. This could potentially cause problems in trying to distinguish climatically-driven lake-level changes from those instigated by temporarily unblocking the sink-holes (e.g. by earthquakes). Finally, the modern lake (Pamvotis) was described, along with a brief review of the present natural vegetation of the at·ea. 3. METHODS 3.1 INTRODUCTION The extreme length of borehole sequences such as 284 pose serious logistical problems when it comes to designing a logical and manageable programme of study. The approach taken with 284 was initially to apply a series of relatively quick and simple techniques to the entire core in order to establish an idea of overall structure. Loss-on-ignition (to assess organic matter and carbonate content) and magnetic susceptibility were principally used for these initial broad-scale analyses. These data were then used as a basis for a programme of further, more detailed investigations across selected intervals of the core (specifically, the Eemian and the last glacial - Holocene transition). These included both physical and chemical techniques, such as particle-size analysis, isotope geochemistry and faunal analysis. All of these methods are described in detail below. 3.2 PHYSICAL ANALYSES 3.2.1 Core Recovery and Logging Core 284 was recovered by IGME in 1989 using a rotary EDECO truck-mounted drill. Retrieved in 3m lengths, it was first logged and then sectioned longitudinally into quarters. One of these quarters (average 50mm across) was then split into metre lengths and archived in open wooden boxes; the remainder was discarded. The core boxes were stored in an unheated shed where the core lengths were able to air-dry. Prior to its transfer to Cambridge, the core was re-logged and compared with the IGME record. Detailed inspection by eye (using a hand-lens) was complemented by the use of dilute HCI and a Munsell soil colour chart (Munsell Color, 1975) in appraising moist sediment. METHODS.22 3.2.2 Magnetic Susceptibility Mass specific magnetic susceptibility (X) is a measure of the ratio of magnetisation induced in a sample to the intensity of the applied magnetising field (Yu and Oldfield, 1989). Essentially, it is a measure of the magnetisation of a sediment sample from the temporary application of a weak (low-amplitude) magnetic field. The strength of the signal is dependent upon the concentration, grain-size and grain-shape of the magnetic minerals within the sample. In some cases, these minerals can form directly within the lake itself. Usually, however, they are derived from weathered-out detrital material from the catchment. One of the main applications of magnetic susceptibility is therefore as a proxy indicator for inwash (Thompson et al., 1975). During warm periods, vegetation flourishes, binding the ground surface, reducing the amount of detrital material washed into the lake from natural erosion. During colder periods, however, reduced vegetation cover results in higher rates of erosion, consequently leading to higher levels of inwash (Thompson et al., 1975). This is discussed in more detail in section 7.2.3. Another application of magnetic susceptibility is in providing a means of correlation between cores taken from the same basin (e.g. Thompson, 1973; Thompson et al., 1975; Dearing et al., 1981; Flower et al., 1984). Even in catchments where the bedrock is lacking in primary magnetic minerals (such as karstic terrain), pedogenically enhanced soils can provide a source of secondary magnetic minerals (e.g. Longworth et al., 1979; Dearing, 1979; Flower et al., 1984). At Ioannina, core 249 was originally studied for pollen by Tzedakis (1991), but no susceptibility measurements were made at that time. Sampling of both cores (284 and 249) was therefore undertaken as part of this study in an attempt to correlate the two records. Sampling was carried out on both cores at approximately 1m intervals. In the case of core 284 , the samples were intended to double for both palaeomagnetic and magnetic susceptibility determinations (a full discussion of the palaeomagnetic work is given in section 3.2.3, below). Cubes of sediment were carefully cut from the cores using a saw blade and trimmed to size with a stainless steel penknife before packing into 2.3cm2 clear plastic sample cubes (8cm3 internal volume) and securing with clingfilm. The sediment cubes were oriented so that their way-up could be marked on the plastic cube faces for the purposes of palaeomagnetic measurement. A total of 318 samples was taken. In the case of core 249, only loose sediment sub-samples from the original core were available (courtesy of P.C. Tzedakis). Sediment was therefore crushed and packed into clear cylindrical plastic pots (IOcm3 internal volume). A total of 153 METHODS.23 samples was taken from this core. The mass of the sediment sample in each case was determined by accurately measuring the mass of the pot before and after packing. Mass-specific susceptibility is calculated using the following expression: reading - background average Xlf = ---=----=-----=-- mass (g) where Xlf = low frequency mass-specific magnetic susceptibility (m3kg- I); and backgroUl'ld average = (meter reading + previous reading) / 2. Susceptibility measurements were made on a Bartington Magnetic Susceptibility Meter MS2 attached to a dual frequency Bartington Sensor MS2B (set to low frequency). Background levels were determined using a clean, empty pot (cubic or cylindrical, as appropriate) . 3.2.3 Palaeomagnetic Analysis The magnetic field of the Earth has the charateristics of a dipole magnet and is thought to be generated from motion within the fluid outer core. Although it has been known since the middle of the 19th century that volcanic rocks acquire a magnetisation on cooling (e.g. Delesse, 1849; Melloni, 1853), it wasn't until the beginning of this century that it was recognised that some older lava flows preserved a magnetisation with a reversed polarity (e.g. David, 1904; Brunhes, 1906). Although the mechanism is poorly understood, it is now well established that throughout geological time the polarity of the Earth's magnetic field has periodically reversed, the last major reversal occurring~780ka ago (Shackleton et al., 1990; Baksi et aI., 1992). Since these reversals occurred almost instantaneously and were global in nature, their recognition in both terrestrial and marine sequences has been important in establishing worldwide correlations and a lengthy chronological framework. It was hoped that by studying the palaeomagnetic signal from the Ioannina sequence, a comparison of reversals could be made with a 'master' global magnetostratigraphy, thereby deriving an independent chronology. The results from that investigation are presented and discussed at length in section 5.4. The methods used are detailed below. The suitability of the Ioannina material for palaeomagnetic measurement had initially to be considered. It is all too easy to analyse a sequence without giving full METHODS.24 consideration to potential problems that might bias results (e.g. Kukla and Zijderveld, 1977; Verosub, 1982; Lszjvlie, 1989). Ideally, sequences should be continuous and undisturbed. If sediments have been subject to subsequent tectonic activity, which has folded or tilted initially horizontally-lying deposits, then magnetic measurements uncorrected for these effects will be misleading. Bioturbation can affect the orientation of magnetic grains within the sediment, with the result that magnetic measurements will again be misleading. Sites with high sedimentation rates are therefore preferable, since any bioturbation effects will be minimised. Finally, coring techniques should minimise disturbance of the sediment and recover vertically­ aligned cores, so allowing accurate orientation of the samples. The Ioannina 284 core satisfies most of these criteria. The sequence appears to be continuous since there are no obvious lithological breaks or hiatuses (section 4.1.1). Whilst . the site is located within a tectonically-controlled basin, it is thought that the sediments have not suffered much post-depositional disturbance. There is no direct evidence to suggest that the sub-basin through which 284 was cored was subject to any tilting or folding as a result of basin subsidence. Discrete lithological bedding, which has a consistently horizontal orientation, occurs in places throughout the length of the core. The proposed pollen-derived age model (discussed in detail in section 5.2) allows an estimation of accumulation rates. It appears that sedimentation was rapid, an average of O.5rnka- 1 (in some cases more), far higher than in most marine environments... It is likely, therefore, that bioturbation effects were minimal, especially since 284 is thought to have originated from the deepest sub-basin. This was a location that would have always experienced relatively little benthic activity in comparison to shallower littoral areas of the lake. Finally, given the nature of the coring equipment, it is a reasonable assumption that the cores were drilled vertically and were subject to minimal disturbance. A total of 318 samples were collected for analysis from the same horizons already analysed for loss-on-ignition and carbonate content were taken (i.e. -lm intervals). Samples were cut from the core using a steel saw blade and were 'way-up' oriented within plastic sample cubes (2.3cm3). Palaeomagnetic measurements were made at the University of East Anglia (under the supervision of Dr B.A. Maher) using a Cryogenics Consultants Ltd. cryogenic magnetometer, utilising GM400 software (version 5.4) and fitted with three SQUID devices. Samples were measured in two­ position mode throughout. A comprehensive summary of this technique is given by Collinson (1983). The drilling method originally employed meant that it was impossible to determine the azimuthal orientation of the core, automatically precluding any declination measurements. Consequently, the two most important METHODS.25 parameters measured by the cryogemc magnetometer were the inclination and intensity of the magnetic field. Initially, the natural remanent magnetisation (NRM) of each sample was measured. This is a vector quantity, described by the inclination, declination and intensity of a magnetic field. The NRM of each sample is a vector sum of the primary remanence (acquired when the sediment was originally formed) and any secondary remanence (that may have been acquired at a later stage) . The primary remanence is the most important component of the NRM, since it is a record of the direction and intensity of the ambient magnetic field of the Earth at the time of sediment formation. Identification and removal of the overprinted secondary remanences is a major part of any palaeomagnetic analysis. There are several ways in which a sediment can acquire a secondary remanent magnetisation, the main ones being depositional (DRM), post-depositional (PDRM) , chemical (CRM) and viscous (VRM). DRM is acquired by magnetic grains as they settle in the water column, which become oriented in the direction of the ambient magnetic field. PDRM is acquired by magnetic grains after burial if they are free to rotate within the interstitial voids of the sediment, aligning themselves with the ambient magnetic field. CRM is again a post-depositional process and relates to those magnetic minerals that undergo chemical change during diagenesis, thereby acquiring a magnetisation. VRMs are generally thought of as time-dependent isothermal remanences (Jacobs, 1994). In other words , magnetic grains within a sediment can gradually acquire a (generally weak) remanent magnetisation in the direction of the ambient magnetic field without being heated. The rate and degree of magnetisation is dependent upon the temperature and grain size (Jacobs, 1994). Sediments can easily acquire VRMs in a variety of ways, such as during coring, sampling or long-term storage. A series of pilots from the entire core (15 samples) were selected and subjected to both alternating field (AF) and thermal stepwise demagnetisation procedures. A brief description of each of these techniques now follows; a more detailed account can be found in Tarling (1983). AF demagnetisation tries to isolate the primary magnetisation from the secondary by randomising the magnetisation directions of those magnetic particles within the sample that have low coercivities. Coercivity is a measurement of the ease with which the magnetisation direction of a particle can be induced to follow that of an applied magnetic field. It is often the case that secondary magnetisations of a specimen are carried by particles with low coercivities. If the magnetisation of these particles can be randomised so that they do not contribute to METHODS. 26 the external magnetic field of the sample, then the remaining remanence is likely to represent the primary magnetisation. The process involves tumbling each sample along the axis of a coil through which an alternating electric current is passing (the tumbling ensures that all alignments of the sample are rotated into the peak magnetic field induced along the coil axis) . The coil and sample tumbler are themselves located within an area in which the ambient geomagnetic field has been zeroed. The field is steadily reduced from an initial strength (measured in milliteslas, mT). The magnetisation of those magnetic particles within the sample having a lower coercivity than the applied field will follow the direction of the field. Steady reduction of the field strength means that the magnetisations of these particles will become effectively 'frozen' in the specimen in random orientations (once the field strength drops below the coercivity values of individual particles). Those magnetic particles with coercivities higher than the initial field strength will remain unaffected. The remanence of the sample is measured after each sample, after which the initial field strength is increased and the procedure repeated. Careful analysis of sample behaviour throughout this stepwise demagnetisation can often reveal the point at which only the primary magnetisation remains. Thermal demagnetisation operates in a similar way to AF demagnetisation, except that it relies on the relaxation times of the magnetic particles rather than the coercivity. Relaxation time, a temperature and grain-size related property, is a measurement of the time required for a magnetic particle to aquire a magnetisation in the direction of an applied field. Samples are heated to a predetermined temperature and maintained at that temperature for a certain period of time. On cooling (in a zeroed external magnetic field) the magnetisation of those magnetic particles with low relaxation times will effectively lie in random directions and will therefore contribute nothing to the external magnetic field of the sample. Those particles with higher relaxation times will be unaffected and so retain their original magnetisation directions. Repeated cycles of heating, cooling and measurement of remanence, with the target temperature being increased stepwise for each cycle, allows assessment of the point at which only the primary magnetisation remains. Different minerals (including magnetic ones) become unstable at specific temperatures and form new minerals that are stable under the altered conditions. For example, goethite alters to haematite at temperatures in excess of -200"C and haematite alters to magnetite at temperatures in excess of -550°C (Tarling, 1983). Chemical stability of the sample is therefore monitored throughout the demagnetisation procedure by measuring its low­ field magnetic susceptibility prior to beginning each new cycle. Once the susceptibility of a sample changes dramatically there is little point in continuing with METHODS.27 the demagnetisation procedure, since its magnetic characteristics will now be determined by a new mineral assemblage. The pilot samples were all subjected to AF and thermal demagnetisation procedures. Stepwise AF demagentisation was carried out at 5mT, lOmT, 20mT and then at 20mT increments up to 100mT. Stepwise thermal demagnetisation was carried out at 50°C increments between lOO-400°C. Results indicated that the thermal method was more successful in removing any overprinted secondary remanences. A blanket demagnetisation was therefore applied to all of the core samples (300°C maintained for 15 mins) and their remanences remeasured. The results are presented and discussed at length in section 5.4. 3.2.4 Particle-Size Analysis The particle-size characteristics of sediment sampled from selected parts of the core were examined by means of a Malvern Instruments Mastersizer-X laser analysis machine. By selectively removing the carbonate and organic fractions of the sediment by chemical means and re-running the particle-size analysis each time, the individual grain-size characteristics of each fraction could be established. Approximately 5g of sediment was sampled from the core at 1m intervals. This material was placed in a polythene test-tube with deionised water and left overnight in a warm (90°C) water bath to completely disaggregate. The resulting solution was then whirlimixed and a small sample immediately placed in the analyser and measured. The residue was centrifuged and excess water decanted. Hydrochloric acid (7%) was then added (to remove the carbonate fraction) and the tube returned to the water bath. Once all reaction had ceased (usually after about 30 minutes), the tube was again centrifuged, excess liquid decanted and deionised water added. Following whirlimixing, a small sample of the solution was placed in the analyser and measured. The residue was again centrifuged and excess water decanted. Hydrogen peroxide (lOO volume) was then added (to remove the organic component) and the tube returned to the water bath. Once all violent reaction had ceased, the tube was left for several hours in the water bath until all further reaction had stopped. After centrifuging and decanting once more, deionised water was added, the solution whirlimixed and a small sample immediately placed in the analyser and measured. METHODS.28 3.2.5 SEM Analysis Interpretation of particle-size data can be greatly enhanced by the use of a scanning electron microscope (SEM), enabling the actual viewing of the individual constituent grains. In addition, the shape and surface textures of the grains can be used to assess the composition and proportion of sediment that is either allogenic or authigenic in origin. Selected sediment samples were disaggregated by adding deionised water and leaving them in a warm (90°C) water bath overnight. On the basis of the particle-size data, the resulting solution was wet sieved into two fractions (>125).lm and >57-125).lm) and dried. The fraction smaller than 57).lm was discarded. The dried material was placed onto an adhesive SEM stub and coated with carbon prior to analysis. Samples were viewed at the Multi-Imaging Centre, University of Cambridge, using a Philips XL30 FEG SEM fitted with an ISIS energy dispersive X-ray microanalyser. 3.2.6 Modern Faunal Analysis During September 1994, eleven sites around the shore of the lake were selected on the basis of accessibility and variation in habitat (fig. 3.1) . Qualitative samples of molluscs were taken from all micro-habitats at the lake edge (e.g. water, shore, on aquatic and terrestrial vegetation) and preserved in plastic tubes and bags for later identification. The sites are described in appendix A. Qualitative ostracod samples were acquired by taking mud samples from the shallows «75mm water depth) and storing in ethanol in sealed plastic containers for later analysis. On return to the laboratory, the samples were dried, sieved and picked using the method outlined below for the fossil fauna. 3.2.7 Fossil Faunal Analysis Samples for faunal analysis were taken at approximately 20cm intervals through those parts of the sequence singled out for detailed study. Slices of sediment 4cm thick were taken from the core, the full width being needed because of the minimal amount of material available (section 3.2.1). A few grams of the sample were retained for possible future analyses (e.g. pollen, diatoms, further magnetic susceptibility). As the fossil fauna was to undergo further chemical tests (stable isotope determinations and METHODS. 29 N i Lake Pamvotis o 2km Fig 3.1 Modern sample sites (described in appendix A). Stippling denotes areas of dense Phragmites reeds. The locations of two springs are also shown. METHODS. 30 so forth), the sediment was disaggregated using purely mechanical means. The largest part of the sample was immersed in deionised water for 24hrs before undergoing repeated gentle freeze-thaw cycles. Commonly, samples required two full freeze-thaw cycles to effect adequate disaggregation. Once broken down, samples were dried and sieved into four size fractions (>lmm; 0.5-1mm; 250J.lm- 0.5mm; and <250J.lm) for faunal analysis. Each size fraction was weighed prior to picking. Samples were picked under a Wild binocular microscope (up to lOOx magnification) using a triple-O sable-hair paint brush, moistened with deionised water when necessary. Specimens (molluscs, ostracods and so forth) were systematically separated from the sediment fractions, identified to species level where possible, counted and stored either in glass tubes (molluscs, macrofossils and so on), or on cavity slides (ostracods). In accordance with conventional practice, only those gastropod molluscs with intact apices were counted (non-apical fragments were counted only where a species was otherwise unrepresented). In the case of bivalve molluscs, complete valves or hinge fragments were counted. For ostracods, the first 350 valves were counted (and the picked fraction weighed if this did not constitute the entire sample). 3.3 CHEMICAL ANALYSES 3.3.1 Sediment Geochemistry According to Dean (1981), the sediments of temperate hard-water lakes (such as Ioannina) can be broadly considered as consisting of four main components : carbonate minerals (usually low-Mg calcite); detrital clastic material (derived from the catchment); biogenic silica (mostly diatomaceous material); and organic matter. lones and Bowser (1978) recognise three distinct mineral sources from which these components are derived: allogenic material (minerals derived exclusively from outside the lake); endogenic material (minerals derived from processes occurring in the water column); and authigenic material (allogenic and / or endogenic material that has undergone a degree of alteration due to post-depositional diagenetic processes. Distinguishing between these three mineral sources is often extremely difficult. In particular, distinguishing between endogenic and authigenic fractions (even using advanced chemical techniques) can be almost impossible. For the purposes of this study therefore (and in the interests of clarity), the definition of Engstrom and Wright METHODS. 31 (1984) is adopted throughout, in which the term authigenic is used to refer to all material formed within the lake, whether by strictly authigenic or endogenic means. Many techniques exist for analysing the chemistry of sediments. Most are bulk methods that do not distinguish between allogenic and authigenic components (Mackereth, 1966; Pennington, et al., 1972; AlIen, 1974; Engstrom and Wright, 1984; Robinson, 1994). With the development of techniques such as inductively-coupled plasma spectrometry, fractionation procedures have been increasingly employed that selectively digest the sediment in a stepwise fashion, permitting allogenic and authigenic components to be measured (e.g. Engstrom and Wright, 1984). However, these methods are time-consuming and were thought inappropriate for the length of core considered here. Since a combination of particle-size and SEM techniques can often be used to assess qualitatively the relative proportions of these two components within a sediment, two geochemical methods were selected that offered a realistic and efficient use of time: loss-on-ignition (to determine broad-scale variability) and bulk sediment isotope analysis (for detailed examination of selected parts of the record) . (a) Loss-an-Ignition Variations in the organic matter and carbonate content of lake sediments are often correlated with changes in organic productivity of the lake system over time. The relative validity of this assumption is discussed at length in section 7.2. Measurement of these components by loss-on-ignition is a relatively simple and standardised laboratory procedure. Sediment samples of approximately 19 crushed weight were initially taken every 1m down the core. Finer resolution was later achieved by sampling the top lOOm of the core at 10cm intervals and the remaining 219m at 20cm intervals. Determinations were carried out using a method slightly modified from Dean (1974) and Bengtsson and Enell (1986), as outlined below. After drying to constant mass in an air-circulation oven (lOYC for 12hrs), samples were burned in porcelain crucibles in a muffle furnace (Gallenkamp FSE-520) for 7hrs at 550°C to determine the loss-on-ignition. All masses were measured to an accuracy of ±O.OOlg. The change in mass provides an approximation of the organic matter content of that sample (Dean, 1974). In calcareous sequences, various conversion factors from loss-on-ignition to organic carbon have been suggested. Generally organic carbon is taken as 40-60% of the loss-on-ignition (Bengtsson and METHODS.32 Enell, 1986). In this study, no conversion factor has been applied to the data since an accurate value has yet to be determined. The ash residues were then burned for a further 7hrs at 950°C to determine the carbonate content. The change in mass (caused by evolution of CO2), multiplied by a conversion factor, reflects the carbonate content of that sample (Dean, 1974). Because of the variable volatility of carbonate compounds, the value obtained is only an approximation of the total carbonate content of the sample and does not allow the exact proportion of different carbonate compounds in the sample to be determined. Consequently, the conversion factor is generally taken to be 1.36 (Bengtsson and Enell, 1986), corresponding to the molecular weight of C03 (60) divided by the molecular weight of CO2 (44). In areas where the carbonate mineralogy of the sediment can be shown to be exclusively low-Mg calcite, a higher conversion factor (2.273) is sometimes advocated, corresponding to the molecular weight of CaC03 (lOO) divided by the molecular weight of CO 2 (44). X-ray diffraction studies of the modern lake sediments at Ioannina (Conispolatis et al., 1986) have demonstrated that low-Mg calcite is the dominant carbonate mineral, whereas high-Mg calcite and dolomite (a magnesium carbonate) are present in only tiny amounts (average 3.1 % and 0.4% respectively). This is not surprising, given the lack of dolomites in the catchment and the overall chemistry of the lake waters (section 4 .2.2) which does not favour magnesium carbonate precipitation. Although a case could have been made for using the higher conversion factor in this study, the lower value has been used throughout, in order to make allowance for the possibility of minor amounts of magnesium carbonate being present. Values quoted for carbonate content are therefore likely to reflect minimum levels. Another potential drawback of this method is that clays within the sediment contain lattice-bound water (in the form of OH- ions). This is generally evolved at temperatures exceeding 550°C (Dean, 1974). In substantially clay-rich sediments, therefore, this loss of water could contribute substantially to the overall loss in mass of the sample. At Ioannina, however, the clay fraction of the sediment is not a major constituent (section 4.1.3). Evolution of lattice water is therefore assumed to have had a negligible effect on the overall loss in mass of the sample. The efficacy of the loss-on-ignition procedure was tested periodically throughout the study. A replicate set of samples from successive levels were taken after every 400 or so determinations to be measured at a later date. Results were then compared. All tests (for both organic matter and carbonate content) returned covariance r-values greater than 0.9. A typical example is shown in fig. 3.2. 178.0 178.5 :g .<:: 179.0 i5.. <1.l Cl 179.5 180.0 o METHODS.33 • Original ................... Replicate Covariance: ,. = 0.93 5 10 15 20 Carbonate Content (%) Fig. 3.2 Replicability of loss-on-ignition technique to calculate carbonate content 178.0 Covariance: ,. = 0.99 178.5 LOI Calcimeter 179.0 179 .5 180.0 5 10 15 20 25 30 35 Carbonate Content (%) Fig. 3.3 Comparison of loss-on-ignition and calcimeter techniques to calculate carbonate content. METHODS. 34 To test the efficacy of the loss-on-ignition procedure as a robust indicator of relative change in carbonate content (as opposed to variation in absolute values), a replicate set of samples was measured using a calcimeter (at the Department of Geography, University of Cambridge). This relied on the evolution of CO2 from a known mass of sample at a known temperature and pressure after the addition of hydrochloric acid. The calcium carbonate values were calculated and compared with the values measured by the loss-on-ignition method. A remarkable correspondence between the two procedures was recorded (shown in fig. 3.3), with a covariance between the two curves of 0.99. (b) Sediment Isotope Geochemistry The study of stable oxygen and carbon isotopes from lakes where primary (i.e. authigenic) carbonates form has become a standard procedure in many palaeolimnological studies. Principles that are routinely applied in marine palaeoenvironmental research have increasingly been applied to lacustrine settings, with varying degrees of success (see review by Kelts and Talbot, 1989). Although some studies have used bioclastic material (such as mollusc and ostracod shells) as a primary carbonate source (see section 3.3.3 below), the technique used here concentrates on the authigenic carbonate fraction that has been produced either by direct precipitation from the water column, or as a result of inorganic biogenic precipitation. Coupled with a detailed knowledge of the regional and local factors affecting a specific lake system, stable oxygen and carbon isotope curves have been used to infer such criteria as variations in air and water temperatures (e.g. Eicher and Siegenthaler, 1984; Siegenthaler and Eicher, 1986), lake level history (e.g. lohnson et al., 1991), residence time of lake water (e.g. Stuiver, 1970), variations in evaporation, precipitation and moisture sources (e.g. Stuiver, 1970; Siegenthaler and Eicher, 1986) and changes in palaeoproductivity (e.g. McKenzie, 1985; Schelske and Hodell, 1991). An excellent review by Talbot (1990) discusses the relative merits of the technique and places particular emphasis on using the degree of covariance between 81S0 and 813C to characterise different hydrological systems. Details of the methodology used in this study are given below. A minimum 20mg of calcite was required for analysis. For each level, approximately 3g of sediment was sampled and added to a solution consisting of 40ml deionised water, plus 40ml of 40 volume hydrogen peroxide (to assist in sediment disaggregation) and stirred occasionally. After 24hrs, the resulting solution was again stirred, passed through a 150/lffi sieve (to remove any detrital mineral grains and / or METHODS.35 fossil fragments), filtered via a Buchner funnel and rinsed with deionised water. The filter paper was then dried and the remaining solids transferred to a plastic tube. The stable isotopes were measured at the NERC Isotope Geosciences Laboratory, Keyworth. Carbonates were reacted off-line with phosphoric acid at 25°C, with the resulting CO2 samples measured from the manifold of a VG SIRA or VG OPTIMA mass spectrometer. Correction of results to the V-PDB scale was by comparison with laboratory marble standards calibrated against NBS-19. Analytical precision for both 8180 and 813C was better than 0.1 %0. By convention, isotope ratios are not given as absolute values, since they would be very small and vary only slightly. Instead, they are given in delta notation as relative deviation (per mil, %0) from the isotopic ratio of a standard (Craig, 1957). Thus, the oxygen isotope ratio 180/160 is given by the expression: {PB 0 = R Slllllple - RSf(/lIdll rd xl 00 R stalldard where R is the absolute ratio of 180 ;'60 . The standard used for both 8180 and 813C in the case of the Ioannina samples was V -PDB, Vienna - Peedee Belemnite (based on carbon dioxide collected from belemnites [Belemnitella americana] of the Cretaceous Peedee Formation of South Carolina). 3.3.2 Modern Water Chemistry An appreciation of the modern water chemistry of the lake is essential if meaningful palaeoenvironmental reconstructions are to be attempted. Only by understanding how the current limnic system operates can trace-element and stable isotope data derived from fossil material be properly interpreted. To this end, a sampling programme was initiated that enabled several parameters of the modern water chemistry to be determined either directly in the field or later in the laboratory. Water samples were analysed from each of the 11 faunal sampling sites . Temperature, pH, conductivity, dissolved oxygen content and alkalinity were determined immediately . A 60ml unfiltered sample was taken for the purposes of later oxygen isotope analysis. A 130ml unfiltered sample was taken and 20ml BaCh­ NaOH solution added (to precipitate the total dissolved inorganic carbonate, TDIC) for the purposes of later carbon isotope analysis. Two 60ml filtered samples (0.45flm micro-pore filter) were taken. One was kept chilled for later use in the field METHODS. 36 laboratory; the other was acidified using O.lml concentrated nitric acid and kept for later trace element analysis. At the end of each day, a Hach portable DRJ700 analyser was used to determine values of nitrate, sulphate, silica and phosphate from one the 60ml samples from each site. Other variables noted at each site included the depth at which the water samples were taken, the extent and nature of terrestrial and aquatic vegetation, turbidity of the water, nature of the substrate, evidence for human disturbance, the general topography of the sample site, the weather and time of sampling. Water samples retained for stable isotope analysis were sent to the NERC Isotope Geosciences Laboratory in Keyworth. The 0180 and oD values were measured relative to V-SMOW (Vienna - Mean Standard Ocean Water); oI3C values of TDIC were measured relative to V-PDB (as above) . Water samples retained for trace-element determination were measured by means of a Jobin Yvon JY-70 Plus inductively-coupled plasma - atomic emission spectrometer (ICP-AES) at Kingston University. A full review of this technique can be found in Jarvis and Jarvis (1992) . A proprietary computer program (PCWATEQ, updated from Truesdell and Jones, 1974) was used to analyse the results. By using other sampling data (temperature, pH and so on), the accuracy of the field and laboratory measurements could be assessed by the calculation of an ionic charge balance error. The program also calculated the salinity (expressed as TDS, total dissolved solids), mineral speciation in the water and the corresponding saturation index. 3.3.3 Ostracod Shell Chemistry Fully calcified ostracod valves are well established as an important source of authigenic carbonate and it has long been known that their chemical composition accurately reflects that of the water at the time of shell formation (see comprehensive review in Holmes, 1996). The trace-elements magnesium and strontium can be linked, with care, to changes in salinity and temperature of host waters (e.g. Chivas et al ., 1983; De Deckker et al., 1988; De Deckker & Forester, 1988; Holmes et al., 1992; Palacios-Fest et al., 1994). Stable isotopes of oxygen have been shown to covary with salinity and temperature in hydrologic ally closed lake systems (e.g. Gasse et al., 1987; Lister, 1988; Schwarcz & Eyles, 1991), whereas stable carbon isotopes can be related to palaeoproductivity (e.g. McKenzie, 1985). Chivas et al. (1993) demonstrated that by combining trace-element and stable isotope data the salinity, METHODS. 37 temperature and chemical history of such lake systems can be determined more successfully than by using anyone technique in isolation. Problems have been encountered with the trace-element analyses on the Ioannina fauna. One of the main criteria for selecting suitable ostracod valves for trace­ element measurement, is that they should be fully adult. Ostracods are tiny (commonly sub-millimetre) bivalved crustaceans. Like all Crustacea, they grow episodically by shedding their carapaces at intervals during their lifetime. There are usually eight moult stages (known as instars) between egg and adult, denoted A-I (largest) to A-8 (smallest). It has been shown that the uptake and concentration of trace-elements (particularly magnesium) in the shell varies during the lifetime of the animal (Chivas et al., 1983, 1986; Palacios-Fest et al., 1994), due in part to its variable growth rate. As a result, most workers advocate the use of fully adult valves in order to obtain comparable results. The ostracod fauna in core 284 contains a relatively low proportion of adults (the significance of which is discussed in section 6.3.4), effectively precluding the use of trace-element geochemistry as a valid technique in this instance. No such restrictions apply when considering stable isotopes. Although relatively little work has been done on the isotopic variability between different moult stages, preliminary results (e.g. Heaton et al., 1995) have shown no significant differences. Nevertheless, for the purposes of this study, it was decided to sample the same moult stages (A-2 / A-3) throughout wherever possible, in order to minimise any complications from this source. Another important criterion for selection is that the same species should be measured throughout. Work has shown clearly that different species often either have different modes of life (e.g. Eyles and Schwarcz, 1991), occupy different microhabitats (e.g. Heaton et al., 1995), or display seasonal preferences when moulting (e.g. Xia et al., 1993; von Grafenstein et al., 1994), resulting in variable isotopic signals. The issue of whether to analyse a single ostracod valve at each level, or to analyse bulked samples (consisting of several valves per level) is another important consideration. Some authors (e.g. Eyles and Schwarcz, 1991; Dettman et al., 1995; Heaton et al., 1995) have analysed single valves. Since ostracods form their shells over a period of time that can often be measured in hours (Turpen and Angell, 1971), they capture a record of environmental conditions that is both highly temporally and spatially specific. Single valve analysis can therefore potentially reveal detail that is lost when valves are bulked (providing only an 'average' signal). However, Xia et al. (1993) and Heaton et al. (1995) warn that since isotopic variation invariably exists METHODS. 38 between individual ostracods, caution must be exercised when using this method. They advocate a sampling strategy similar to that employed in the analysis of oceanic for a minifera, namely replicating measurements at each level (usually three individual valves are used). Where the selected ostracod species is too small to be measured using single valve analysis (or it is not desirable to do so), bulking of valves from each level is commonly undertaken. The 'average' isotopic signal derived in this manner must be interpreted in terms of the period of time that the thickness of each sediment slice represents. For example, Schwalb et al. (1994) examined 2cm slices of sediment from a core drilled in Lake Neuchatel, Switzerland, that represented between 25-30 years of deposition. Dettman et al. (1995), on the other hand, analysed samples at 20cm intervals from a series of cores from Lake Huron, that corresponded to 40-100 years of deposition. Another criteria that needs to be considered is the preservation of the valves. Material that appears to have undergone any post-depositional dissolution or carries evidence of calcite overgrowth should be avoided. The weight of valves is also important. Modern mass spectrometers can now measure samples that are only a few tens of micro grams in weight. Nevertheless, even when single-valved analyses are being carried out, the process is made easier if the species being used is relatively large or has a thickly calcified shell. The preparation of ostracods for geochemical analysis is an intensely laborious process. It is essential that only authigenic carbonate is examined (i.e. the ostracod valve), so any adherent carbonate material must be removed, as must any residual organic matter. Most workers clean the valves manually under a binocular microscope, using high purity deionised water and a fine paint brush (after Holmes, 1992) . This is often accompanied by additional procedures, either to help disaggregate the sediment initially, or to help remove organic matter. These include roasting in a vacuum (e.g. Lister et al., 1991), roasting in an oxygen plasma (e.g. Boomer, 1993), or applying various strengths of dilute hydrogen peroxide (e.g. Curtis and Hodell, 1993; Schwalb et al., 1994; von Grafenstein et al., 1994, 1996). In the absence of a detailed investigation into the relative effects of different cleaning methods on isotopic variability, purely physical methods were used throughout this study. Sediment slices (4cm thick) were taken from the core at approximately 20cm intervals. The sediment was disaggregated, sieved and picked according to the method set out in section 3.2.6. Between 8-10 valves were selected per level for METHODS. 39 isotopic analysis of Candona permanenta (all either A-2 or A-3 instal's). All surface contamination was removed by means of a fine paint brush and high purity deionised water. The valves for each level were then placed into a small glass bucket, moistened with a small quantity of deionised water and crushed into tiny fragments. Stable isotopes were measured at the NE RC Isotope Geosciences Laboratory at Keyworth. Samples were reacted on-line with phosphoric acid at 90°C in a VG Isocarb coupled directly to a VG OPTIMA mass spectrometer. Correction of results to the V -PDB scale was by comparison with laboratory marble standards calibrated against NBS-19. Analytical precision for both 8180 and 8 13C was better than 0.1 %0. 4. RESULTS This chapter presents the results of the physical and chemical analyses of the core material. There are two exceptions: results of the palaeomagnetic analyses are presented in chapter 5, since they relate directly to the chronology of the corej and the results of the faunal analyses (modern and fossil) are presented in chapter 6. Interpretations are discussed at length in chapter 7. 4.1 PHYSICAL ANALYSES 4.1.1 Lithological Description The lithologies of core 284 are detailed in table 4.1. It will be noted that from 8.44m to the bottom of the core, the lithology is a relatively homogeneous olive-grey silt. The subtle changes that occur within this main unit are detailed in table 4.2. Depth (m) 0-1.36 1.36-5.85 5.85-7.50 7.50-8.44 8.44-319.0 Description Brown calcareous silt with limestone clasts «7cm) . Very stony in places. Olive-grey clayey silt. Below -2.53m shell fragments seen (including Dreissena, Bithynia and Valvata). Dark greyish brown calcareous silt, very shelly in parts. Olive-grey calcareous clay, containing abundant tiny shell fragments. Olive-grey silt, calcareous in parts . Munsell Colour 10YR 4/3 5Y 412 2.5Y 312 5Y 412 5Y 412 Table 4.1 Description of the lithologies of core 284. Munsell colours determined on moist sediment. No distinct lithological breaks were detected in the core, despite careful examination. All changes in lithology (limited to the top -8.5m) were across apparently conformable and gradual boundaries. Apart from a missing section of core between 164-164.50m (due to mechanical problems experienced whilst coring), the sequence appears to be continuous. Depth (m) 8.50-14.50 -18.50 26.10-26.40 29.0-29.50 31.75-34.80 42.0-45 .50 66.0-66.35 -72.0 -90.0 95.42-95.48 125.20-144.0 -160.0-178.0 164.0-164.50 172.6-172.9 -192.0 264.10 -270.0-305.0 308.0-309.50 311.75-313 .30 Description Slight change in colour from maIn sediment (no lithological change). Very shelly. Becomes slightly less shelly below this point. Darker, fossiliferous bed present with abundant Dreissena, along with lower numbers of Bithynia, Viviparus and Valvata. Bithynia opercula also common. Returns to occasionally shelly below this bed. Red-brown mottling within sediment. Very shelly, with beds of Dreissena. Very shelly, with beds of Dreiss ena. Viviparus also present. Sediment non-cohesive and soft whilst coring. Valvata and Only occasional shell fragments seen below this point. Abundant ostracods, but no molluscs. Organic material present, including wood fragments. Occasional molluscan shell fragments . Between 140.2- 140.5, fairly shelly bed, with Dreissena common. Subtle reduction in clay content , becoming slightly sandier. Occasional fine organic bands noted over this interval, along with occasional yellow-brown mottiing, especially between 165-169m. Missing section of core (poor recovery for this drive) . Slightly shelly bed. Clay component Increases slightly . Ostracods still abundant. RESULTS. 41 Munsell Colour 2.5Y 3/2 5Y 212 5YR 4/4 2.5Y 6/4 Thin (-3cm) band of olive-brown clay. 2.5Y 4/4 Occasional plant debris noted. Colour change to very dark grey. No lithological change. 5Y 3/1 Light olive-brown mottling. 2.5Y 5/4 Table 4.2 Detailed litho logical description of core 284, from 8.50-319m (see text for further details) . Munsell colours determined on moist sediment. RESULTS. 42 According to the limited data available from IGME regarding the degree of recovery of the original cores, the lengths within each metre compartment of storage box represented successive metre drives, even if the overall length of material did not exactly measure 1m. As described in section 3.2.1, the entire core had been air-dried, which had often resulted in fragmentation. The accuracy of any depth measurement made as part of this study is therefore subject to some degree of error. Since the preservation and quality of the core varies throughout, the degree of error also varies. However, it is estimated that at worst, depth values are accurate to ± lOcm, although for the majority of the sequence, a value of ±5cm is considered more realistic. 4.1.2 Magnetic Susceptibility The mass specific magnetic susceptibility results for the whole core are presented in fig.4.1. Generally speaking, values average around 1.5x10-7m3kg- 1, which can be considered low. In comparison, Longworth et al. (1979) measured values ranging between 60-120x10-7m3kg- 1 from the bedrock limestones of the Lac d' Annecy region and Flower et al. (1984) measured values of 40-160x10-7m3kg- 1 from sediment cores recovered from the Dayat-er-Roumi catchment in Morocco. In the Kopais Basin, nearly 200km SE of Ioannina, AlIen (1986) attributed her low susceptibility values of between O.6-2.8x10-7m3kg-l to the high proportion of calcite in the sediment (up to 93%) and accordingly applied a correction factor. In the case of Ioannina, however, carbonate content (presumed to be dominantly calcite) rarely exceeded 25% (see section 4.2.1 below), so the dilution effect of diamagnetic calcite is likely to be negligible and no correction factor has been applied. Low susceptibility values are therefore presumed to reflect either a low initial concentration of magnetic particles within the catchment soils, a low proportion of detrital material reaching the central lake site of core 284, or a combination of both. Between approximately 165-220m, susceptibility values are much higher (peaking at nearly 19x1O-7m3kg- 1 at 180.20m). Detailed examination of the sediment over this interval revealed the increased concentration of small, black aggregated iron-rich nodules (averaging -1-2mm diameter) that were rare elsewhere in the sequence (see SEM results, below). Further analysis of these nodules was undertaken to test whether they were responsible for the high susceptibility values at these levels . Several nodules were picked from the sediment, packed together in clingfilm and then placed in an empty susceptibility measuring pot (suspended in the centre of the pot, again using clingfilm). Their mass specific susceptibility was measured (using the method outlined in section 3.2.2) on a low frequency setting. The mass of the sample RESULTS. 43 0.0 0.0 10 .0 10 .0 20 .0 20 .0 30 .0 30 .0 40.0 40 .0 50.0 50.0 60 .0 60 .0 70 .0 70.0 80.0 80.0 90 .0 90 .0 100.0 100.0 110 .0 110 .0 120 .0 120.0 130 .0 130 .0 140 .0 140.0 g 150.0 150 .0 g -5 -5 0.. ., 160 .0 160.0 0.. Cl ., Cl 170 .0 170.0 180.0 180 .0 190.0 190.0 200.0 200.0 210 .0 210.0 220 .0 220 .0 230.0 230 .0 240.0 240 .0 250 .0 250.0 260.0 260 .0 270.0 270.0 280 .0 280 .0 290 .0 290 .0 300.0 300 .0 310.0 3 10.0 0 5 10 15 20 -I 0 2 3 Magnetic susceptibility Magnetic susceptibility Fig. 4.1 Magnetic susceptibility profile of core 284 (sampled every -1 m) . Left-hand graph shows entire data set. Right-hand graph shows enlarged horizontal scale to illustrate lower amplitude variability. Magnetic susceptibility units are X 10-7 m3kg-l• RESULTS. 44 was O.013g, the volume was -27mm3 and the meter reading (after subtracting background levels) was 23 .3. Because the volume of the sample was much less than a standard pot, a 20% correction factor was applied. Using the equation outlined in section 3.2.2, a mass specific magnetic susceptibility value of 2. 16xlO-5 xlO-7m3kg-' was obtained. This value is reasonably close to that obtained from the iron oxide minerals magnetite (5xlO-5 xI0-7m3kg-') or maghaemite (4x10-5x10-7m3kg-'). The origin of these potential carriers is discussed in section 7.2.3. To determine whether these high susceptibility values were associated with catchment erosion rather than any other process, the frequency dependent susceptibility of the original sediment samples was calculated, using the following relationship: where Xfd % = frequency dependent magnetic susceptibility; Xhf = high frequency mass specific magnetic susceptibility; and X'f = low frequency mass specific magnetic susceptibility. Commonly expressed as a percentage of total low frequency susceptibility (as here), frequency dependent susceptibility indicates the delayed response of viscous magnetic grains at the stable single domain/superparamagnetic grain-size boundary to the applied magnetising field (Yu and Oldfield, 1989). The original data are shown in table 4.3. The results (all values reasonably close to zero) suggest that the carrier in these levels (magnetite/maghaemite, as identified above) is fine-grained, of single domain and most likely to be of detrital origin (L.P. Zhou, pers. comm.) . It is therefore probable that these magnetic grains derive from the weathering of specific horizons in the catchment (most likely from within the flysch) and may represent times of increased pedogenic enhancement under 'Mediterranean' climatic conditions. This interpretation is discussed further in section 7.2.3 . Similar peaks can also be easily distinguished in the magnetic susceptibility curve for core 249 (fig. 4.2). Although the sampling resolution was not as fine as for 284 (due to the availability of remaining sub-samples), several major points of correlation between the two records are distinguishable. For example, the peak at 111 .50m in 249 is directly correlated with the peak at 180.20m in 284. Other peaks are matched as shown. By using major susceptibility variations to correlate the two cores, the pollen data and chronological framework from 249 can be related to 284. This is discussed at length in section 5.2.2. RESULTS. 45 10 20 30 40 50 60 70 80 90 100 § ..c:: 0.. <1) 110 Cl 120 130 140 150 160 170 180 190 0 5 10 15 20 25 Magnetic Susceptibility Fig. 4.2 Magnetic susceptibility profile of core 249 (sampled every -Im). Magnetic susceptibility units are X 10.7 m3kg- 1• RESULTS. 46 Depth (m) Xhr Xlr Xrd (%) 180.20 18.79 18.93 0.74 181.35 10.40 10.48 0.76 182.60 12.29 12.39 0.81 183.30 12.01 12.08 0.58 184.75 16.30 16.42 0.73 185.70 9.85 9.95 1.01 Table 4.3 Mass specific and frequency dependent magnetic susceptibility values for selected levels in 284. Units of Xhfand Xlr are x 1O.7m3kg·' . A detailed chemical analysis of these grains was beyond the scope of this study, but spectral analysis (using an X-ray micro analyser attached to the SEM) indicated a dominantly iron oxide composition, with a coating of silica (see SEM analysis results, below). The aggregated grains were composed of individual angular octohedral particles less than half a micron in size (illustrated in plate I, fig. A). These results support the suggestion that the magnetic carrier is a fine-grained, detritally-derived ferrimagnetic iron oxide such as magnetite/maghaemite. It is not clear whether this is the same carrier as for the rest of the sequence, where much lower values are the norm. This may be a reflection of much lower concentration levels, the presence of a different carri~r, or may indicate an authigenic source, such as from magnetotactic bacteria (e.g. AlIen, 1986). Preliminary X-ray diffraction (XRD) analyses carried out by P. Rowe (UEA) in conjunction with the U-series dating work (section 5.6) reveal the presence of both goethite and magnetite between 83-100m. Further detailed rock magnetic analyses, coupled with additional XRD analyses and a comprehensive study of grain-size distributions, are necessary to determine the nature of the carrier(s) throughout the entire core. 4.1.3 Particle-Size Analysis Particle-size analysis of the sediment was carried out between 11 0-7 Srn. The age model (developed in chapter 5) suggested that this interval spanned the end of the penultimate glaciation (MIS-6) and the whole of the Eemian (MIS-Se). A range of material from full glacial to full interglacial could therefore be analysed. 80~ 81 82 83 80 81 82 83 84 84 85 85 86 86 87 87 88 88 g 89 89 g .<: 90 c.. 91 .., Cl 92 90 .<: 91 c.. .., 92 Cl 93 93 94 94 95 95 96 96 97 97 98 98 99 99 100 100 101 101 102 102 I I I I I I I I I I I I I I I I I I I I I I I I I I I I I I I I I -2 -1 0 1 2 3 4 5 6 7 8 9 10 -2 -1 0 1 2 3 4 5 6 7 8 9 10 30 25 20 15 10 5 0 Phi Units Phi Units Carbonate Content (%) Total Raw Sediment Isolated Carbonate Fraction Fig. 4.3 Particle-size data. Left-hand graph shows total sediment data, sampled at lm intervals. Centre graph shows isolated carbonate fraction, also sampled at lm intervals. Right-hand graph shows total carbonate content as measured every lOcm by the loss-on-ignition method, plottede in reverse. ~ ~ ~ • .j::>. -..l RESULTS. 48 The particle-size data are presented in fig . 4.3 . The plots represent typical particle­ size distributions for the raw sediment and the isolated carbonate fraction . The raw sediment plot suggests that the lithology for this interval should be classified as a fine silty sand (the silt - sand boundary is taken to be 4<1>, 63~m). This interpretation is slightly at odds with the visual examination (section 4.1.1), which classified the sediment over this interval as being a clayey silt (i.e. much finer). Subsequent SEM analysis (see below) confirmed that the sediment consisted largely of aggregated grains (composed of fine silt- and clay-sized particles), bound together by means of a siliceous cement. SEM analysis also confirmed that the procedure used to disaggregate the raw sediment was not sufficient to break all of the aggregated grains into their component particles. The siliceous coating could clearly act as a capable cementing agent. Only extended mechanical rinsing of the sediment fractions through a succession of finer sieves was found to be effective in separating the aggregated grains. As a result, the particle-size plots, as they stand, are biased towards a coarser overall grain size, although the relative distribution of size classes is likely to still be applicable. The overall grain-size distribution bears a good relation to the carbonate curve for the same interval (generally interpreted as a proxy for productivity), the implications of which are discussed in section 7.2.1. As might be expected, the isolated carbonate fraction plot also correlates well with the carbonate content curve (fig. 4.3). In general, however, the main feature of the plots is that between approximately 100- 85m, interpreted as being a 'warm' phase corresponding to the Eemian (section 5.8), the dominant particle-size coarsens noticeably. It is clear from this preliminary study that there is considerable scope for further detailed grain-size analyses. Future work might initially reassess the results of this study in light of the surprising resilience of the siliceous cement in holding the aggregated particles together. A more accurate idea of the difference in grain-size distribution between glacial and' interglacial periods could then be obtained. It should be possible to pick up some evidence of aeolian input, particularly during glacial phases. The soil profiles of the region display a marked bimodal distibution (see section 2.3), with a coarser, quartz-rich silt-sized fraction becoming more dominant during glacial periods (van Andel, in press). It is thought that this represents increased aeolian input from source areas such as North Africa and, possibly, from the loess deposits in central Europe. RESULTS. 49 4.1.4 SEM Analysis SEM analysis of the sediment between llO-75m was used to investigate several of the specific questions posed by the particle-size results (in particular, the nature and grain size of the carbonate fraction) . In general, most of the sediment was composed of aggregated grains of fine silt-sized carbonate particles, clay minerals and a high proportion of fine siliceous material (including diatom fragments) . The grains were coated in silica, suggesting a post-depositional diagenetic effect (probably due to percolating groundwaters) that was responsible for aggregating and cementing the smaller sedimentary particles together. A minor contribution (in the order of a few percent) to the total sediment by detrital material in the 'colder' levels was evidenced by occasional feldspar, quartz and limestone grains that showed signs of abrasion due to transport. Plate I, fig . C, shows a typical aggregated grain from 89.02m. Some of the carbonate crystals are shaped on a range of scales like hexagonal plates, reminiscent of mica 'books'. Some larger ones are illustrated in plate I, fig . D. They are typical of carbonates that have precipitated rapidly in waters with a very low concentration of magnesium (Folk, 1974). Other carbonate crystals within the aggregated grains display a more irregular polyhedral morphology, also typical of low-Mg, low salinity lacu~trine precipitates (e.g. Kelts and Hsti, 1978). Other components of the sediment included silica-coated pollen grains (a typical Pinus grain is shown in plate I, fig . B) and framboidal iron sulphide spherules (plate I, fig. E) . These latter are often formed in the uppermost few millimetres of lake sediments where relatively low-energy environments of deposition coincide with a source of metallic ions and decomposing organic matter (e.g. Vallentyne, 1963; Wiltshire et al., 1994). Under these quiet, locally anoxic conditions , microbial activity (both iron reducing and sulphur reducing) helps to form the authigenic (sensu stricto) spherules within the sediment. Several iron sulphide mineral species have been identified as forming spherules under these conditions (including marcasite, pyrrhotite and melnikovite), however, the most commonly found is pyrite (FeS2). A detailed chemical analysis of the spherules was beyond the scope of this study, although the X-ray microanalyser attached to the SEM clearly demonstrated that they were iron sulphides. They were therefore assumed to be pyrite. Several aggregated black mineral grains recovered from those parts of the sequence with high magnetic susceptibilities were also analysed under the SEM. They were composed of many tiny individual grains, less than half a micron in diameter (plate I, RESULTS. 50 fig. A). The X-ray micro analyser indicated that they were iron oxides, coated in a si1ca cement. The distinct octagonal crystal form displayed by many of the grains is typical of minerals such as magnetite, an iron oxide identified as one of the potential magnetic carriers in this part of the core (section 4.1.2). 4.2 CHEMICAL ANALYSES 4.2.1 Sediment Geochemistry (a) Loss-an-Ignition Despite the lithological homogeneity of the core, the loss-on-ignition curves show a high degree of structure (figs. 4.4 and 4.5). Because of the high number of data points (n = 1,972), a nine-point running mean has been applied to smooth both curves and reveal some of the more dominant aspects of their structure. As explained in section 3.3.1, the loss-on-ignition curve for 550°C indicates variability in the organic matter content of the sediment. A verage values decrease from about 6% at the bottom of the core to about 4% at about lOOm. After this, values leap to an average of between 8-10% for the remaining part of the record. Superimposed on these broad-scale changes are higher-order oscillations. For example, the top lOOm exhibits substantial variation, as does the lowermost 80m. There are also distinct peaks in organic matter content centring around 190m and l50m. The loss-on-ignition curve for 950°C indicates variability of carbonate content in the sediment. Values vary between about 2% to 40%, although as with the organic matter content curve, higher order variability is clearly superimposed on more broad-scale first-order changes. Unlike the organic matter curve, the base-line average does not appear to gradually decrease upwards, but remains constant at around 5%. Smaller scale variability (in terms of wavelength) is obviously more complex than for the organic matter curve. A comprehensive interpretation is therefore given in chapter 7, where the connection between carbonate content and aquatic productivity is discussed at length. A composite plot of organic matter and carbonate contents is presented in fig. 4.6. RESULTS. 51 0 0 10 10 20 20 30 30 40 40 50 50 60 60 70 70 80 80 90 90 100 100 110 110 120 120 130 130 140 140 150 150 g g 160 160 .s .s 0. 0. <\) 170 170 <\) Cl Cl 180 180 190 190 200 200 210 210 220 220 230 230 240 240 250 250 260 260 270 270 280 280 290 290 300 300 310 310 0 5 10 15 20 25 0 5 10 15 20 Organic Matter Content (%) Organic Matter Content (%) Fig. 4.4 Organic matter content, sampled every 10cm for the top 100m, every 20cm for the remainder (n = 1,972). Left-hand graph shows raw data, right-hand graph shows smoothed data (9-pt. running mean). RESULTS. 52 0 0 10 10 20 20 30 30 40 40 50 50 60 60 70 70 80 80 90 90 100 100 110 110 120 120 130 130 140 140 150 150 § 160 160 § .s 170 170 .s 0. 0. (!) (!) Q Q 180 180 190 190 200 200 210 210 220 220 230 230 240 240 250 250 260 260 270 270 280 280 290 290 300 300 310 310 0 10 20 30 40 50 0 10 20 30 40 Carbonate Content (%) Carbonate Content (%) Fig. 4.5 Carbonate content, sampled every 10cm for the top lOOm, every 20cm for the remainder (n = 1,972). Left-hand graph shows raw data, right-hand graph shows smoothed data (9-pt. running mean). RESULTS. 53 0.0 10.0 20.0 30.0 40.0 50.0 60.0 70.0 80.0 90.0 100.0 110.0 120.0 130.0 140.0 :§: 150.0 160.0 .<: 0.. I!) 170.0 Cl 180.0 190.0 200.0 210.0 220.0 230.0 240.0 250.0 260.0 270.0 280.0 290.0 300.0 310.0 o 10 20 30 40 50 60 70 80 90 100 Percent of Total Sediment Fig. 4.6 Summary loss-on-ignition plot showing organic matter (stippled), carbonate content (shaded) and inorganic matter (white). -7 82 83 84 85 86 87 88 89 g 90 ..c 0.. 0) 91 Cl 92 93 94 95 96 97 98 99 100 101 -3 -2 -I o 2 8 13C (%0) -6 3 4 8180 (%0) -5 -4 -3 -2 82 83 84 85 86 87 88 89 90 g ..c 91 0.. 0) 92 Cl 93 94 95 96 97 98 99 100 101 Fig. 4.7 Stable isotopes between lOO-83m derived from bulk carbonates. Isotope values quoted relative to V-PDB. Zonation details given in text. ::>;:, ~ ~ 2:l • Ul .j:>. RESULTS. 55 (b) Sediment Isotope Geochemistry The stable isotope results derived from the analysis of bulk sediment carbonate between 83-100mare shown in fig. 4.7. Values of 8I3C and 8 180 are both given relative to V-PDB. 8I3C varies between about +3.5%0 and -2.3%0, whereas 8180 varies between about -2.2%0 and -6.2%0. Covariance between the two curves is reasonably strong (r = 0.58). The similarity in the behaviour of both curves allows the plot to be split into several discrete zones for the purposes of description. The interpretation and significance of these data is discussed at length in section 7.4.2. lOO-98.Sm 8I3C values oscillate initially between about +0.5 and +3%0, before falling to fluctuate around 0%0. Over the same interval, 8180 oscillates around -3.5%0. 98.S-96.0m 8 I3C values decrease rapidly at the very beginning of the zone from around 0%0 to -2 .1%0 (at 98 .02m), before increasing gradually to around -0.5%0. Values increase slightly at the end of the zone. The 8 180 values display a similar pattern, decreasing to a minimum of -6%0 at 98.02m and then increasing to -3.8%0 at 96.80m. However, the 8180 then undergoes a second oscillation before the end of the zone. 96.0-90.90m Values of 8 13C remain at a fairly constant level throughout (--0.8%0), although values are slightly lower from about 92.5m. The values of 8180 gradually decrease at about 93 .lOm from an average of around -4.5%0 to an average of -4.8%0. 90.90-86.10m 8 I3C falls sharply at the beginning of the zone, from values of around -0.8%0 to -1.2%0 and then increases steadily throughout (except for a single point at around 88m) to a value of about -0.75%0. Values of 8180 also decrease at the beginning of the zone, although more slowly than 813C. With the exception of the same point at about 88m, the value of 8180 remains roughly constant at around -5.2%0. 86.10-83.0m Values of 8I3C fall sharply at the beginning of the zone and then oscillate around -0.5%0, followed by a very sharp increase to +3.5%0 at 83.5m. Values of 8180 decrease slightly at the beginning of the zone, then increase gradually until they repeatedly oscillate (to maximum of approximately -2.2%0) from 83 .80m. The isotopic signature of two bedrock samples was also analysed. One sample consisted of limestone pebbles collected from site 2, located on the north-eastern shore of the lake. The other sample consisted of limestone bedrock recovered from RESULTS. 56 the base of core 256 (the marginal core drilled to the south-west of 284), at a depth of 132m. The results were as follows: Site 2 material Core 256 bedrock OBC +1.97%0 +1.37%0 0180 -1.04%0 -2.63%0 As before, 013C and 0180 are quoted relative to V-PDB. Faure (1986) suggests that the majority of marine carbonates from Cambrian to Tertiary age have 013C values close to zero (relative to PDB). He also suggests that 0 180 values for marine carbonates are commonly between +20-30%0 (relative to SMOW), depending on age. The carbonates in the Ioannina catchment are all marine Mesozoic limestones (described in section 2.2) and the differences between the two measured samples can be explained if they represent limestones of different age. The 256 sample is likely to be the Upper Senonian Limestone that underlies the majority of the basin. The site 2 material could be derived from any of the limestone outcrops along the northern shore and could therefore be of Mid-Jurassic - Cretaceous in age. The ol3C values of both samples are broadly in accordance with values that might be expected from marine carbonates of these age, as are the 0180 values. The conversion between 0180Y_SMOW and 0180Y_PDB is given by the equation: Thus, the bedrock samples have 0180 values (relative to V-SMOW) of +29.78%0 and +28.12%0, completely in accordance with the expected values suggested by Faure (1986). 4.2.2 Modern Water Chemistry The composition of the modern waters are typical of a temperate hard-water lake, being dominated by Ca2+ and HC03- ions. Table 4.4 shows the major chemical parameters of the lake (full details are given in appendix B). As might be expected in a karstic area, the lake is reasonably alkaline, having a pH that averages 7.64, a salinity that averages 0.35%0 (i.e. freshwater) and an Mg/Ca ratio that is low, at 0.34. The results are discussed at length in section 7.4.1. 'C' ~ Cl CoO -10 ........ -----------:-.'---...." .' ... -20 -30 -40 -50 I I I I -60 -10 I I I I I I I I /// :/ MWL/ I I I I ,./ .. " ..... ,. ... ,. .... 6 ,','" I.:~:/ /' -7 .5 I -5 Gradient = 4.8 1 -2.5 818 0 (%0) o RESULTS. 57 Fig.4.8 Modern lake waters . 0 180 and oD both relative to V-SMOW. MWL = Meteoric Water Line. -3 .. -4 -5 11. -6 3. 'C' -7 ~ 7. u <"l CoO -8 -9 -10 -11 -1 2 6. I -8 -6 -4 -2 o 8180 (%0) Fig. 4.9 Modern lake waters . 0 180 relative to V-SMOW, ol3e relative to V-PDB. "I RESULTS. 58 Site 8180 813C 8D Mg Ca Na K pH Salinity 1 -0.7 -3 .8 -13 10.37 38.76 19.77 3.49 7.53 0.27 2 -0.5 -3.5 -12 10.38 44.02 20.01 3.43 7.48 0.27 3 -0.6 -6.1 -12 10.39 52.78 20.72 3.07 7.77 0.41 4 -0.5 -3 .2 -12 9.99 40.00 19.74 3.37 7.42 0.37 5 -0.4 -3 .6 -12 10.06 39.81 19.67 3.51 7.53 0.30 6 -7.0 -12.4 -43 5.39 70.37 57.93 0.60 7.64 0.54 7 -1.1 -7.4 -14 14.21 91.70 25.26 1.64 7.83 0.56 8 -0.6 -4.0 -12 10.11 40.20 19.08 3.46 7.53 0.27 9 -0.6 -3 .8 -12 10.30 41.23 19.33 3.44 7.72 0.28 10 -0.5 -3.5 -13 10.01 39.00 18.94 3.48 8.09 0.29 11 -0.4 -5 .0 -12 10.14 39.57 19.44 3.28 7.54 0.33 Table 4.4 Summary of water chemistry data for modern sites. 8180 and 8D values in per mil (%0) relative to V-SMOW. 8 13C values in per mil (%0) relative to V-PDB . All trace element values in mg/I. Salinity values in %0 (calculated as Total Dissolved Solids, TDS). See text for details. The stable isotope measurements indicate that for the most part, the waters are relatively homogeneous (fig. 4.8). They lie on an evaporation trajectory (gradient -4.8) from the meteoric water line (MWL) for the Mediterranean. This has a slightly different gradient from the global MWL, given by the equation oD = 8 x 0 180 + 20 (Gat and Carrni, 1970). Values of oI3C are given relative to V-PDB. Values of 0180 and oD are given relative to V -SMOW. The covariance between the 0180 and the oI3C values is reasonably strong (r = 0.91), illustrated in fig . 4.9. The significance that this has for interpreting the hydrological status of the lake is discussed in section 7.4.1. Although this is the first isotopic study of the waters from Lake Pamvotis , the trace­ element results are comparable with those obtained by Marinos (1974) and Overbeck (1980). In particular, Overbeck (1980) notes the eutrophic status of the lake and the high levels of silica, which he attributes to the influence of siliceous material in the catchment. 4.2.3 Ostracod Shell Chemistry The ostracod stable isotope results are presented in fig . 4.10. Only ostracods from the top 25m of the core were measured (corresponding approximately to the period from just before the Last Glacial Maximum into the Holocene: see chapter 5). Insufficient valves were preserved from the Eemian section of the core (approximately 100-84m) to allow isotopic determinations to be made. As with previous carbonate RESULTS. 59 0 0 2 2 3 3 4 4 5 5 6 6 7 7 8 8 9 9 g 10 10 g .s 11 11 ..c: Cl. i5.. C1.l 12 12 C1.l Cl Cl 13 13 14 14 15 15 16 16 17 17 18 18 19 19 20 20 21 21 22 22 23 23 24 24 25 25 -5 -4 -3 -2 -1 0 -3 -2 -1 0 2 3 4 8 l3e (%0) 8180 (%0) Fig. 4.10 Stable isotope results derived from ostracod shell calcite (quoted relative to V-PDB). Raw data in thin solid line joined by points; smoothed data (3-pt. running mean) in heavy black line. RESULTS. 60 818 0 (%0) -3 -2 -I 0 2 3 3 4 4 5 5 6 6 7 7 8 8 9 9 IQ IQ 11 11 12 12 § 13 13 § -5 ..c 0. 14 14 P. 0) 0) Cl Cl 15 15 16 16 17 17 18 18 19 19 20 20 21 21 22 22 23 23 24 24 -5 -4 -3 -2 -I 0 Fig. 4.11 Comparison of smoothed stable isotope results (3-pt. running mean) derived from ostracod shell calcite (quoted relative to V -PDB). Covariances: below ISm, r = 0.31 ; above ISm, r = 0.75. RESULTS. 61 measurements, 813C and 8180 values are given relative to V-PDB. Three-point running means have been applied to both curves for the purposes of clarity and to minimise noise. The oxygen curve varies over about 6%0 (from approximately +3%0 to -3%0), although the smoothed curve reduces the overall variability to about 4%0. The 813C curve varies over about 5%0 (approximately 0 to -5%0), although again, the overall variability is reduced to about 3.5%0 by the smoothing. Overall covariance between the curves is generally weak (r = 0.37 for the raw data; r = 0.54 for the smoothed data). The two smoothed curves are compared in fig. 4.11. However, covariance varies between different parts of the record. Below 15m the curves covary with an r-value of 0.31. Above 15m, however, the r-value improves to 0.75. The possible significance of this is discussed in section 7.4.3. Duplicate sets of valves were sampled at selected intervals to test for replicability of results. Values were plotted as straight averages between the two determinations where appropriate. Lack of sufficient material meant that it was not possible to carry out enough measurements for the comparisons to be statistically significant. Therefore, whilst the results are shown in table 4.5 for the sake of interest, they have not been included in the final data set. It is clear that whilst the replicability of the 8l3C is reasonable in two of the cases, the third value and at least two of the 8180 values exhibit marked differences. It is likely that this is related to the variation inherent within the samples themselves, as each 4cm slice of sediment at this level is thought to represent at least 40 years (see chapter 5). These results highlight the necessity for further duplicate measurements, so that a statistically valid estimate of isotopic variability within samples can be calculated. Several duplicates were also used to compare different methods of removing contaminant organic matter from the sample. These entailed either using 40 volume hydrogen peroxide in the disaggregation stage, or vacuum roasting the sample (420°C, lO·lmbar, for 30 minutes) prior to isotopic measurement. The results, compared to the manual brush cleaning method used as the standard technique in this study, are shown in table 4.6. Once again, insufficient measurements were made for the results to be considered statistically significant and therefore the values were not included in the final data set. It appears that whilst there is some evidence to suggest that the peroxide pre-treatment has a relatively minor effect on 8l3C, its effect on 8180 is considerably more marked. The vacuum roasting treatment appears to significantly affect both 813C and 8180, suggesting that caution is needed in its application. As outlined in section 3.3.3, different workers employ a diverse range of preparation and pre-treatment techniques. There is clearly an urgent need to develop a standard pre- RESULTS. 62 treatment method (similar to that now used in foraminiferal studies) based on rigorous quantitative analyses of large data sets. Depth (m) No. Valves Average Average 13.82 8 -3.77 -2.50 13.82 6 -3.74 -3.76 -1.52 -2.01 .... .... .......... ......... . ......... . ........ . .. . .. ........ .... .. ........ ....................... .. ............. ..... ... . . . ......................... " ••• ,', ........... . . . .. . . . .... . ....................................... 000 16.80 9 -1.53 -1.21 ......... .. ... ~. ~:. §.9. .............................. ? ............................... :.~.: .1.9 ................... .... .... :.~.:.1. T ............... .. ......... :.9.:.?} .......................... :.9.:.7.~ ....... ... .. . 23.0 23.0 9 9 -2.12 -1.76 -0.55 -1.94 -0.35 -0.45 Table 4.5 Comparison of duplicates. No. of valves = number of valves cleaned and used in a single sample. o l3C and 0180 values quoted as per mil (%0) relative to V-PDB. See text for details. Depth (m) 16.80 16.80 No. Valves 12 12 PN P V -1.52 -1.80 Variation 3.4 22.4 -1.62 -1.13 VaI"iation 125.0 56.9 .. ........ ... ~.~:.§9. .................. ... .. ........ ? ...... ... .. .. .. .............. M ....... ... ..... .. :}.:1T .................................................. :9.:7.~ .... .. .......... .......................... . 21.20 21.20 12 12 P V -2.26 -2.20 26.2 22.9 -1.40 -1.60 141.4 175.8 ........... }.~:}9. ................... .... ...... .. ? ........... .................. M ................. :J.:7.? .................................... ......... .. .. .. :9.::?§ .. ................ ....................... .. 23.0 23.0 12 12 P V -2.09 -2.16 7.7 11.3 -0.63 -1.10 40 144.4 ....... ....... ~.~:9. ................................ ? ............................. M ................. :}.:~1 ................................................... :9.:1? ...................................... ... .. 23.79 23 .79 23.79 12 12 9 P V M -3.27 -2.78 -3.46 5.5 19.6 -0.55 -1.46 -0.03 1733.3 4766.7 Table 4.6 Comparison of ostracod preparation treatments. No. valves = number of valves cleaned and used in each single sample. P = hydrogen peroxide treatment. V = vacuum roasting treatment. M = manual brush cleaning. ol3C and 0180 values quoted as per mil (%0) relative to V-PDB . Variation = % variablity of values from the M-value (taken to be the 'true' value) . See text for details . RESULTS. 63 4.3 SUMMARY This chapter presented the results of the physical and chemical analyses of the core material, in addition to modern water chemistry determinations. A detailed lithological description of the core was followed by a discussion of its magnetic susceptibility characteristics. Although susceptibility values were generally low, several discrete peaks were identified that were associated with small, black, aggregated grains in the sediment. Further analysis of these grains suggested that they were the source of the high susceptibility values and that they were composed of a ferrimagnetic iron oxide mineral, most probably magnetite/maghaemite. The possible origin of these carriers within the Ioannina catchment under normal Mediterranean climatic conditions was also discussed. The results of the particle size analysis (undertaken between lOO-83m) were then presented. Separate fractions were analysed, consisting of the total sediment, the isolated carbonate fraction, the isolated organic fraction and the remaining 'minerogenic' fraction. Results suggested that the sediment should be classified as a fine silty sand. This was at odds with the visual lithological description of a clayey silt. The difference was explained by observing that the preparation procedure for the particle size analysis was insufficient to completely disaggregate the sediment. Overall results were therefore regarded as being artificially biased towards a coarser grain sizes and should therefore be treated with caution. SEM analyses revealed that · the problem with the disaggregation procedure was caused by a silica coating (probably of diagenetic origin) that cemented the individual grains of the sediment together into composite masses. The grains were largely aggregates of siliceous material (including many diatom fragments), clay minerals and carbonate particles. The carbonate grains were of particular interest, displaying either a polyhedral or a hexagonal structure, indicative of rapid precipitation in fresh waters that had a low concentration of magnesium. Other grains of interest included framboidal iron sulphide spherules (assumed to be pyrite) and the magnetic particles contributing to the intervals of high magnetic susceptibility. Work on aspects of the sediment geochemistry was then presented. Despite the lithological homogeneity of most of the core, the loss-on-ignition procedure revealed a high degree of structure in both the organic matter and carbonate content curves. The isotopic signals derived from bulk sediment carbonates between lOO-83m also revealed a distinct degree of structure, with a relatively strong covariance between RESULTS. 64 813C and 8180 values. It was suggested that this might be indicative of a closed lake system. The results of the modern water chemistry analyses indicate that Lake Pamvotis can be described as a typical eutrophic freshwater temperate hard-water lake, with waters that have undergone evaporation. Reasonably strong covariance between 813C and 8180 values suggested that the modern day lake might also be considered as a closed lake system. Finally, the results from the isotopic analyses of the ostracods from the top 25m of the core were presented. These showed interesting patterns of variability, particularly in their covariance, which markedly improved over the top I5m or so of the record. These results are discussed further in chapter 7, where, along with the age model derived in chapter 5 and the faunal data described in chapter 6, detailed interpretations are suggested and a synthesis of the all the results presented. 5. CHRONOLOGY 5.1 INTRODUCTION Establishing detailed chronological control for long terrestrial sequences is notoriously difficult. Even assuming that the record is continuous (as is the case with Ioannina 284), accumulation rates are likely to have varied between and within glacial and interglacial periods. No single technique exists that will provide a consistent chronology for a core of this age, yet clearly this is essential if any coherent palaeoenvironmental story is to be derived. The simple practice of matching proxy curves from different sequences is clearly unacceptable without some common basis of comparison and independent chronological control. The approach taken in this study is first to attempt a correlation with core 249. A comprehensive pollen-derived stratigraphy exists for the 249 sequence and this has been successfully linked to the marine oxygen isotope record (Tzedakis 1991, 1993, 1994). It is intended that a provisional age-model should be established for 284, based on the chronology derived from 249. Other dating techniques will then applied to the sequence (e.g . radiocarbon, magnetostratigraphy, U-series) in order independently to verify and refine the proposed age-model. Each procedure is now discussed in turn. 5.2 CORRELATION WITH CORE 249 Pollen analyses have traditionally provided a useful method for correlating terrestrial sequences. Although a full palynological study has yet to be undertaken on 284, Tzedakis (1991) carried out a comprehensive study on core 249, located less than a kilometre away and within the same sub-basin (I. Broussoulis, pers. camm.). If a secure basis for correlation with 249 can be established, then the chronology developed for that sequence can be applied to 284. The veracity of the age model established by Tzedakis (1991) for 249 is first discussed, followed by a suggested basis by which the two sequences may be correlated. CHRONOLOGY • 66 5.2.1 Basis of the Age Model for 249 A total of 217 pollen analyses were undertaken for the whole 185.50m length of core 249 by Tzedakis (1991), an average of one every -85cm. Not only was he able to demonstrate the presence of well-preserved pollen throughout the entire core, but he was able to show that the succession of different taxa was cyclic and structured. He was therefore able to propose a zonation of the sequence based on vegetational succession, which essentially represented alternations between forest and open vegetation communities. These higher order changes were interpreted as reflecting shifts in climatic conditions from interglacial to glacial mode. Lower order variability between individual taxa was interpreted as representing vegetational changes within each interglacial or glacial. Temperate arboreal taxa were present throughout even full glacial stages, albeit at low frequencies. This clearly demonstrated that the site was refugial, from which temperate vegetation could expand after climatic amelioration (Bennett, et al., 1991; Tzedakis, 1991, 1993). No independent chronology was established for 249. Instead, a timescale was erected first by means of correlation between the pollen record from 249 and those of the two radiocarbon dated cores drilled at loannina (Bottema, 1974) and then by comparison with three other long European pollen sequences. These are now considered in turn. Two short cores, designated loannina I and 11 (Bottema, 1974), were recovered from the northern part of the basin (fig. 2.1). loannina I was thought to represent the last glacial period and the Holocene, based both on the vegetational succession and three radiocarbon dates (obtained from bulk samples). However, Bottema (1974) suggested that there were problems with accepting the two lower dates, which defined an interstadial that he designated zone T (characterised by high frequencies of Pinus, bracketed by high frequencies of Quercus and Abies). The lowest date of 37,660±930 yrs BP (GrN-6529) was thought to be unsatisfactory because of possible contamination by younger material. Bottema (1974) also suggested that the upper of these two dates, 40,000±1,000 yrs BP (GrN-4793), was too young, despite it being near the limit of the radiocarbon range. In any case, Tzedakis (1991) noted that there was no immediately obvious correlative of this interstadial in 249. The Lateglacial­ Holocene transition in loannina I was dated at 10,190±90 yrs BP (GrN-4875), marking a decrease in Artemisia and chenopods and a corresponding increase in Quercus. This transition was identified in 249 at a depth of 17m. Much of the Holocene record from 249 was absent as the top 10.20m of the sequence was missing (due to extensive previous sub-sampling by IGME). However, the forest phase subsequent to the Lateglacial-Holocene transition in 249 resembled the beginning of CHRONOLOGY • 67 the Holocene record from Ioannina I, being characterised by early rises in Quercus, Ulmus, Corylus and Tilia, with a later rise in Ostrya frequencies (Tzedakis, 1991). Ioannina 11 was thought to extend back to the last interglacial, based on the characteristic vegetational structure of the basal section (very high initial Abies frequencies, followed by high frequencies of Quercus, Ostrya, Ulmus, Tilia and other taxa). Bottema (1974) proposed an Eemian age for this interval, explaining the radiocarbon date of 45,800 +2,5001-1,900 yrs BP (GrN-6181) obtained on bulk sediment as possibly being subject to root contamination. However, the pollen signature of this interval bore no resemblance to any forest periods in 249, including the Eemian. Above this section, a zone devoid of pollen was succeeded by a Holocene sequence that matched Ioannina I. The correlation of 249 with any part of Ioannina I or 11 (with the possible exception of the early part of the Holocene) was therefore extremely tenuous, a point freely conceded by Tzedakis (1991). A strategy for establishing long-distance correlations between 249 and other long European pollen sequences was then proposed. Four important sequences were considered: Tenaghi Philippon, a record from north-eastern Greece, that may extend into the Lower Pleistocene (Wijmstra, 1969; Wijmstra and Smit, 1976; van del' Wiel and Wijmstra, 1987a, 1987b); Valle di Castiglione, a 250ka record from central Italy (Follieri et al., 1988; Narcisi et al., 1992); and the central French records of Grande Pile (Woillard, 1-978; de Beaulieu and Reille, 1992) and Les Echets (de Beaulieu and Reille, 1984, 1989), both of which extend back at least 140ka (Woillard, 1978; Woillard and Mook, 1982; Guiot et al., 1989). Although broad-scale similarities were demonstrated between 249 and all four of these records, only the Tenaghi Philippon correlation will be discussed further here, since the age model for 249 was essentially derived from this sequence. This in turn had been correlated with the marine oxygen isotope record. Tenaghi Philippon is the longest terrestrial palynological record from Europe. Results have been published from two cores, designated TF2 and TF3 (Wijmstra, 1969; Wijmstra and Smit, 1976; van der Wiel and Wijmstra, 1987a, 1987b). TF2 was a 120m long core drilled in the late 1960s through the Philippi Plain, part of the Drama Basin in northeastern Greece. A timescale for the top 30m was initially proposed, based on a series of ten radiocarbon dates derived from bulk sediment (Wijmstra, 1969) and the characteristic structure of the pollen succession. The timescale for the lower part of this core was derived only after it had been correlated with TF3 (van der Wiel and Wijmstra, 1987), for which palaeomagnetic data existed. TF3 was a 280m long core drilled in 1976 approximately 150m northwest of TF2 and was correlated CHRONOLOGY • 68 with it on the basis of vegetational and lithological similarities. Although no radiocarbon determinations were obtained from TF3, a series of palaeomagnetic measurements were made by N.D. Opdyke at Lamont Doherty. Full details have not been published, but they are referred to by van der Wiel and Wijmstra (1987), who suggested that the Brunhes/Matuyama boundary was located at a depth of 134m and another reversal, possibly the Jaramillo, was located occurred 195-210m. This enabled Wijmstra and Groenhart (1983) to propose an age model for TF3 that utilised the radiocarbon dates from TF2 (Wijmstra, 1969), the age of the Brunhes/Matuyama boundary (assumed to be 730ka) and an inferred age of 120ka for the Pangaion interstadial (assumed to be the last interglacial) as control points. In this way, a time­ depth relationship was established and a correlation with the marine oxygen isotope timescale of V28-239 (Shackleton and Opdyke, 1976) was suggested. This age model for the Tenaghi Philippon sequence was later revised slightly (van der Wiel and Wijmstra, 1987a, 1987b), once new biostratigraphical data for north-western Europe became available (e.g. Zagwijn, 1985). Although the choice of suitable control points was limited and not entirely satisfactory from a stratigraphical point of view, it was on the basis of the vegetational comparison with other well established and chronologically robust north-west European records that the final age model could be justified. The proximity and stratigraphical length of Tenaghi Philippon meant that it was the obvious 'yardstick' against which 249 could be compared. Nevertheless, Tzedakis (1991) pointed out several problems when comparing pollen spectra from different sites in ge~eral, and from these two sites in particular. Ioannina and Tenaghi Philippon, although only approximately 350km apart, are subject to markedly different climatic regimes. A changing moisture gradient from west to east (high precipitation in the west, much lower in the east) has a significant effect on the type of vegetation prevailing at anyone time. For example, forest periods in the Tenaghi Philippon record were dominated by Pinus and Quercus. At Ioannina, however, Abies, Fagus, UlmuslZelkova and Carpinus were also significant during these periods. In addition, arboreal taxa were often absent from Tenaghi Philippon during the full glacial, whereas at Ioannina they were continually present during these periods at low frequencies (the significance of which has already been outlined above). Nevertheless, despite these and other problems, a considered and balanced basis for comparing higher order vegetation changes between the two records was proposed, making possible the correlation of several major interglacials and forested interstadials (Tzedakis, 1991). CHRONOLOGY • 69 The possibility was then considered of linking 249 with the marine oxygen isotope record via the correlations established for the Tenaghi Philippon sequence by Wijmstra and Groenhart (1983). The problems of comparing two different parameters were discussed. Strictly speaking, the marine oxygen isotope record is a measure of global ice volume (and to a lesser extent, local temperature) variability (e.g. Shackleton and Opdyke, 1973; Shackleton, 1987). However, it is often taken to be a broad proxy for climatic change, with various odd-numbered isotope stages corresponding to interglacial or interstadial periods and even-numbered isotope stages corresponding to glacial or stadial periods. As Tzedakis (1991) points out, the pollen record is a complex multivariate signal representing a range of factors (climatic, biotic and so forth) that are at best regional in nature. However, with care the summary APINAP curve from a detailed pollen record can also often be interpreted as a suitable proxy for climatic change. High frequencies of arboreal pollen are generally interpreted as indicative of warmer periods, lower frequencies being indicative of colder periods, although this is not always necessarily the case (e.g. Coope et al., 1997). On this basis, comparison of higher order variability between the two climatic proxies (marine oxygen isotopes and APINAP) was considered reasonable, although certain assumptions had first to be taken into account. These included consideration of the response times of terrestrial vegetation and the marine isotope record to climatic change (e.g. Wright, 1984). It was assumed for the purposes of correlation that the response of the two systems was essentially synchronous at the onset of interglacial periods, although as Tzedakis (1991) points out, vegetation may have been responding to a completely different set of climatic variables than those responsible for variations seen in the isotopic record. A more detailed discussion concerning leads and lags between the response times of different systems is presented in section 7.5.4. Tzedakis (1991) then proposed using the age model suggested for the Tenaghi Philippon sequence by Wijmstra and Groenhart (1983) as a 'stepping stone' by which the marine oxygen isotope stratigraphy could be transferred to 249. To improve upon the original correlation, the V28-239 Pacific sequence used by Wijmstra and Groenhart (1983) was rejected in favour of a composite record (V19-30 and V19-28, both from the eastern Pacific) that possessed improved resolution and chronostratigraphical control. Several direct correlations between interglacials recorded in 249 and the marine record were suggested. Despite some uncertainties, particularly good correspondence was demonstrated for the locally-named interglacials Dodoni (with MIS-11), Zitsa (with MIS-7) and Metsovon (with MIS-5e). Because of the generally poor sampling CHRONOLOGY • 70 resolution, the weakest part of the scheme was acknowledged as being between the end of MIS-5 and MIS-1, not surprisingly also the weakest part of the correlation between 249 and Tenaghi Philippon. Other possible correlations were also discussed, particularly for glacial periods. Because a varying degree of uncertainty existed in the correlation of parts of 249 with the marine record, no attempt was made to assign an age to every pollen zone. Tzedakis (1991) was therefore able to propose an age model for the 249 sequence incorporating: a radiocarbon date of 1O,190±90 yrs BP for the Lateglacial-Holocene transition from Ioannina I (Bottema, 1974); a comprehensive correlation with Tenaghi Philippon on the basis of both similarities in AP/NAP structure and vegetational succession within different pollen zones; and a reasonably confident correlation with the marine oxygen isotope record. This tentative chronology suggested that the top 162.75m of the 249 sequence extended back 423ka. Although Tzedakis (1991) discusses at length certain problems that still exist with respect to this age model, given the degree of uncertainty inherent in the dating of any long terrestrial sequence, confidence in his chronology for 249 would seem reasonable. 5.2.2 Correlation of 284 with 249 Because no detailed pollen stratigraphy yet exists for 284, a suitable alternative method for comparing the two sequences must be employed. The procedure using magnetic susceptibility for correlating cores from within the same lake basin is now well established. Thompson (1973) successfully matched susceptibility profiles from a series of cores taken from Lake Windermere in NW Britain. It was later shown that under certain circumstances it was possible to match susceptibility profiles from cores taken from different basins (e.g. Thompson et al., 1975; Dearing, 1983; Dearing, 1986). As mentioned In section 4.1.2, the magnetic susceptibility signal from 284 is generally weak, except for certain levels where markedly stronger peaks are seen. These are thought to represent the inwash from the erosion of discrete horizons within the flysch units (outcropping to the east of the lake) that contain a high proportion of magnetic minerals. The same pattern of distinct peaks is seen in the magnetic susceptibility profile from 249, enabling the identification of a series of time­ synchronous levels in both cores (fig. 5.1). CHRONOLOGY. 71 0 10 10 20 20 284 249 30 30 40 50 40 60 .... 50 70 .. ' 80 60 .. ' ...... 90 100 110 70 80 ? .............. ' ~~=--...... /.//: .... / ... / .. 120 130 90 ................. 140 § 150 -5 0.. 4) 160 Cl 170 180 100 110 120 ..... : ..... ---- ._---------_ .. _------- •••• ~ ••••••••••••••.•••• ::::::::::::::::::~: ~:::::~:: :: ::::::::S· .··· ······ ;i~'/~?::> .••• ••••• ••••• ••• ••••••••• •••••••••• ••••••• •••••. ~ .... ,_ ---- -----.-._----_ ... _-----------_ ... _------._---------- - 130 190 .... ,- 200 140 ? 210 _._ .: ... --_ ... "-- - 220 150 ------ ... _---_ ...... _-_ ... _-- -_ .... _-_ ... -.-. __ ... _--- - - _._- - .. -.. "" ? 230 240 160 --------------------------------J-----~-- ~;;;---~------------ --- ________________ 1 _________________ --- 250 170 260 180 270 280 190 o 2 4 6 8 290 300 Magnetic Susceptibility 310 o 2 4 Magnetic Susceptibility Fig. 5.1 Proposed correlations between magnetic susceptibility profiles of cores 284 (left) and 249 (right). Units for magnetic susceptibility are x107 m3kg- 1. CHRONOLOGY. 72 Using the similarities of the magnetic susceptibility curves as a framework, a correlation can now be suggested based on the comparison of the APINAP curve (and its associated chronology) from 249 with the carbonate content curve from 284 (fig. 5.2). As already mentioned, the APINAP curve in this case is considered to be a first­ order proxy for climatic variability (Tzedakis, 1991). For much of core 284, the carbonate content is largely indicative of lake productivity (section 7.2.1) and may therefore also be considered as a first-order proxy for climatic variability, enabling comparison between the two records . Such a correlation rests on the implicit assumption that both vegetational change and carbonate content respond synchronously to climatic change. In truth, the response times of the two systems are likely to be different and a lead/lag situation would exist. It must be remembered, however, that the sampling of the two cores is not continuous, but instead consists of a series of discrete 'snapshots' at different intervals of time. In addition, the time between 'snapshots' in 249 is not the same as between those of 284. Pollen from 249 was sampled at -85cm intervals, corresponding to a period of - 2ka (average accumulation rate"'" 0.39mka-'). The carbonate content in 284 was determined at 10 or 20cm intervals (section 4.2.1) and represents a much shorter period of time (approximately 200 or 400 years, using an average accumulation rate "'" 0.53mka-'). With such disparity between sampling intervals and the inherent uncertainty that this generates, it is not possible to determine any lead/lag effect that may exist unless much finer sampling is undertaken for both cores. Under the circumstances therefore, it seems reasonable to assume that within the sampling constraints and over the timescales involved, variations in vegetational change and carbonate content are effectively synchronous. A more detailed discussion of leads and lags between the response times of different systems is presented in section 7.5.4. Analysis of the two records (fig. 5.2) reveals a remarkably good correlation for approximately the last 420ka, represented by the recovered part of 249. Beyond this, the age model for 284 can be tentatively extended by extrapolation and comparison of the carbonate content curve with the marine isotope SPECMAP record (Imbrie et al., 1984). In conjunction with the timescale established by Prell et al. (1986), this suggests that 284 stretches back beyond 620ka, into MIS-16. By transferring the chronology of 249 in this way, a working age model for 284 can be established. This is able to serve as an initial framework against which other independently derived age models can be compared. 0 10 20 30 4D 50 60 70 80 90 lOO 110 120 130 14D § 150 -5 0-(1) 160 Cl 170 180 190 200 210 220 230 24D 250 260 270 280 290 300 310 Carbonate Content (%) o 10 '.4 ....•...... ...•••. ..... ::.: . E:;'.::~ ':.',:';.:: ­,., ~;I.~~~;~S·~::~:- "'·~:::·;~~,\t~'.'.\'­ ;.~~'" .. 1r 20 .. -. :~u_:::~':;':~:::; ';r~'" ..... ..... . r' 30 :~~:.:.:."-i:.~~;:~::::~ ..... __ =...:::::==--- ....... ,;~; .. ~rN,;.-.-... " 0°/ {~:.!. \ i i .: ••••••.• ~!' ..... 4;;;::;; .......... . ;:~:::~~ ~~ ~ ~'-. ,~:::~: ........ :::h .--...... ;;:;;~'::-.--.----.-.-.... -.--- ... -.-- ......... . ~ 4D ::~~.:. ==::::;;;~~ ·····:-::·:·:········-----..:f······-··· .. .:I. ..... .... 2 3 4 5 .... .... 6 7 8 CHRONOLOGY. 73 o 25 -.f:::::-' ..... APINAP % 50 75 ..................... ~::;?: :,m;n~::.; . ..... : . ........ :,. .... ~::::::s .. 100 ..... _. ___ ....... ..... -· .... ~::::::!~!t ............ HH;;::; ••..•• ----.- ::::;::,.. <.~' " 10 20 30 4D 50 60 70 80 90 lOO 110 120 130 .......... 9 ... ~,,~t~£,: .......................................... 14D ............................... ~ .... ...... ...... :::::--:.If;;~::\~-' .. .r- _~=~;;;::.. ,:;;~::: :::::;::~ ,.1 .... ...... ; .• :::;1-{: ...•..... __ ..............•..... __ ....... -. ,,' ;. ~~~;;'" 150 160 170 180 -.... ::: ........... . "::~ ............... ::;/~ II ,. }~y~~~~~~~~:::. .~' <' 190 5 o 2 3 4 Magnetic Susceptibility .. .. .. " l::::::':~:;::"" '::~:. -I o 2 3 Magnetic Susceptibility Fig. 5.2 Suggested correlation between the APINAP pollen record from 249 (dashed line, right­ hand graph) and the carbonate content of 284 (dashed line, left-hand graph). Magnetic susceptibility (x 10-7 m3kg- 1) for both cores depicted by solid line. Suggested correlations with marine oxygen isotope stages are shown. § .c 0.. (1) Cl CHRONOLOGY • 74 5.3 RADIOCARBON AGE DETERMINATIONS Radiocarbon dating is a well established technique that can be employed to date organic material that is younger than about 35ka (Evin, 1990). A comprehensive summary of the procedure can be found in Olsson (1986) and Pilcher (1991). Levels selected for dating from the Ioannina 284 record were identified on the basis of significant shifts in the high resolution carbonate record for the top 40m of the core, which appeared to match reconstructed temperature curves for approximately the last 35ka BP (e.g. Atkinson et aI., 1987; Guiot et aI., 1989; de Beaulieu et aI., 1994; Lowe et al., 1994; Walker, 1995; Lowe and Walker, 1997). A preliminary interpretation of the carbonate curve identified the Last Glacial Maximum (LGM), the Late-glacial Interstadial, the Younger Dryas (YD) and the steep rise at the beginning of the Holocene. It was later possible to amend the preliminary interpretation once the results from the faunal analyses (chapter 6), isotopic analyses (section 7.4.3) and pollen analyses (P.e. Tzedakis, unpubl. data) became available. The revised interpretation is illustrated in fig. 5.3 . The sampling strategy was therefore designed to test this age model. As there were no terrestrial plant macrofossils present, the shells and opercula of aquatic molluscs were used for dating (specifically, the gastropods Viviparus janinensis and Bithynia graeca and the bivalve Dreissena (Carinodreissena) cf. stankovici, all of which are described in chapter 6). The small diameter of the core meant that insufficient material was recovered for conventional radiocarbon dating. A series of 12 dates was therefore obtained from a total of 11 levels using the accelerator mass spectrometry (AMS) technique (table 5.1 and fig. 5.3). There is a possibility that the dates, although in stratigraphical order, are nevertheless slightly too old. Such age anomalies may result from reservoir effects that can affect - karstic lake systems, in particular, so-called 'hard-water error' (e.g. Deevey et ai, 1954; Shotton, 1972; Karrow et al., 1984). A certain amount of 'old' carbon derived from the limestone bedrock can become assimilated into the shells of calcareous organisms (such as molluscs), giving rise to an age anomaly which produces a date much older than expected. For example, Harkness (1975) demonstrated that a 5% level of contamination by old carbon would produce a value approximately 400 yrs older than the true age; a 40% level of contamination would increase this error to 4,100 yrs. Since different species of mollusc assimilate different amounts of old carbon, hard-water error can also be species dependent. Roberts (1983) considered the likely contamination of Dreissena shells from the Late Quaternary Lake Konya (Turkey) from old carbon to be significant, but suggested that even a 20% level of CHRONOLOGY • 75 2 3 ® 1,480±45/ 4 1,915±45 5 6 7 . + ::t>. + ~ + tl::l + ...... 0 + Co/) ;;:j ::t>. ::::j Cl :::tl ::t>. '"0 :J:: '"<: • ...... 0 .j>.. FAUNA AND BIOSTRATIGRAPHY • 105 Possibly the most detailed investigation of the malacology at Ioannina was carried out by Dollfus (1922), who examined material collected by Marius Dalloni in 1918 from a site south-west of the village of Katsikas . By comparing the mollusc an biostratigraphy and lithologies with that from other sites in the Balkans (e.g. Corinth, the Megara Basin), the sediments were assigned an Upper Miocene age. This age estimate was subsequently supported by Dalloni (1923). Eight fossil aquatic taxa were identified (discussed in section 6.2.4). Dollfus (1922) also listed eight modern aquatic taxa collected from the lake by Dalloni. In his study of the geological evolution of Epirus and Thessaly, Aubouin (1959) listed nine species of aquatic mollusc collected from the Katsikas site (discussed in section 6.2.4). On the basis of updated faunal comparisons, he thought that the sequence was Lower Pliocene in age. Fossil molluscs were again collected from this site by Rocher­ Bizon and identified by Gillet (1962), who recorded five aquatic taxa. He then went on to review and compare several other similar faunas from sites in Epirus before suggesting an Upper Pliocene age for the deposits. Guernet et al. (1977) returned to the Katsikas site some years later and took samples that were later analysed for pollen, charophytes, ostracods and molluscs. The ostracod fauna is discussed below (section 6.3). Eight molluscan taxa were identified (discussed in section 6.2.4). On the basis of the faunal assemblage, they also suggested that the age of these deposits was Upper Pliocene. Whilst on a recent field tour of Epirus, Reischtitz and Sattmann (1990) visited the Ioannina basin and collected thilty molluscan taxa, of which seven were aquatic. Finally, four species of modern hydrobiids have been described from Ioannina by Schtitt (1962, 1980) and Reischtitz and Sattmann (1990): Semisalsa steindachneri (WESTERLUND, 1902); Belgrandiella (Belgrandiella) haesitans (WESTERLUND, 1881); Horatia (Neohoratia) epirana SCHUTI, 1962; and Paladilhia (Paladilhiopsis) janinensis (SCHUTI, 1962). Their occurrence is limited to the springs and small streams on the northern shore of the lake; they have not been found within the lake itself. Accordingly, they are not considered further in this study, although a comprehensive discussion of the classification of these and other Balkan hydrobiids can be found in Kabat and Herschler (1993). Species Viviparus janinensis (MOUSSON, 1859) Valvata piscinalis (MULLER, 1774) Bithynia graeca (WESTERLUND,1879) Lymnaea auricularia (LINNAEUS, 1758) Lymnaea peregra (MULLER, 1774) Lymnaea stagnalis (LINNAEUS, 1758) Physa acuta DRAPARNAUD, 1805 Anisus vorticulus (TROSCHEL, 1834) Gyraulus albus (MULLER, 1774) Gyraulus janinensis (MOUSSON, 1859) Planorbarius corneus (LINNAEUS, 1758) Ancylus jluviatilis MULLER, 1774 Anodonta anatina (LINNAEUS, 1758) Anodonta cygnea (LINNAEUS, 1758) Dreissena (Carinodreissena) cf. stankovici L'VOVA AND STAROBOGATOV, 1982 Pisidium nitidum JENYNS, 1832 Pisidium spp. Habitat Little ecological infonnation. Likely to prefer deeper water habitats in hard-water lakes. Occurs in ponds and slow running waters, but prefers lakes with abundant aquatic vegetation. Prefers medium to hard-water open lake environments (dislikes stagnant water). Found in standing freshwater bodies, especially lakes in hard-water areas. Found in lakes and slow-flowing rivers, especially in hard-water areas. Found in a variety of fresh-water habitats. Prefers hard-water lakes with abundant aquatic vegetation. Found in marshy or shallow lake environments with abundant aquatic vegetation. Found in a wide variety of freshwater habitats. Prefers lakes with abundant aquatic vegetation. Found in a wide variety of freshwater habitats. Prefers lakes with abundant aquatic vegetation. Little ecological infonnation. Likely to prefer lakes with abundant aquatic vegetation. Prefers freshwater bodies with abundant aquatic vegetation. Found in rapid-flowing rivers or lakes with stony substrates and low levels of aquatic vegetation. Prefers rivers, canals and lakes with sandy substrates in which to bury itself. Prefers rivers, canals and lakes with muddy substrates in which to bury itself. Little ecological infonnation. Likely to prefer shallow, high-energy littoral areas in a variety of fresh-water and brackish environments. Found in lakes, streams and ponds, particularly in hard-water areas. Various, depending on species. See text. Table 6.2 List of aquatic molluscan fauna found during this study, with summarised ecological infonnation. See text for details. Modern I Fossil M/F M/F M/F M F M M F F M/F M M ~ M ~ M ::t.: M/F ;:t.. M/F § tl:I ....... M/F <:) V:l "'"i ::ti ;:t.. :::l <;) ::>::I ;:t.. "t:l ::t:: "'<: • -0 0\ Site 1 Viviparus janinensis Valvata piscinalis Bithynia graeca Planorbarius comeus Lymnaea auricularia Lymnaea stagnalis Physa acuta Dreissena cf. stankovici Anodonta cygnea Site 10 Valvata piscinalis Bithynia graeca Gyraulus janinensis Dreissena cf. stankovici Pisidium spp. FAUNA AND BJOSTRATIGRAPHY. 107 Site 6 Planorbarius comeus Gyraulus janinensis Pisidium sp. Site 7 Viviparus janinensis Pl£morbarius comeus Lymnaea stagnalis Ancylus fillviatilis Site 2 Viviparus janinensis PUmorbarius comeus Lynmaea auricularia Anodonta anatina Lake Pamvotis Site 11 Site 4 Lymnaea auricularia Lymnaea stagnalis Physaacuta Valvata piscinalis Viviparus janinensis PlaJlorbarius comeus Site 8 Gyraulus janinensis Bithynia graeca Fig. 6.1 Sampling sites for modern aquatic molluscan fauna . See text for details. FAUNA AND BIOSTRATIGRAPHY • 108 6.2.1 Systematic Review of the Aquatic Molluscan Fauna at Ioannina A general description of all aquatic mollusc an taxa found at Ioannina (modern and fossil) is now given. Their taxonomy is summarised, along with what is known of their occurrence, ecology and any other relevant details (summarised in table 6.2). The taxonomic nomenclature essentially follows Vaught (1988) unless otherwise indicated. The original citation is given for each species followed by a synonymy that refers only to usage in relation to material from Ioannina. Many of the species are well-known European forms and are thus only briefly described. In considering distribution, emphasis is placed on European (and in particular, Balkan) occurrences. The systematic review is followed by a separate consideration of the modern and fossil assemblages derived from this study and, where appropriate, an assessment made of their biostratigraphical and palaeoenvironmental importance. Class Gastropoda Subclass Prosobranchia Family Viviparidae Genus Viviparus DEMONTFORT, 1810 Viviparus janinensis (MOUSSON, 1859) Plate 11, figs. A-C 1859 Paludina injlata VILLA var. janinensis MOUSSON, Viertel}ahrschr. NatLlIj. Gesell. ZUrich, 4, p.55. 1922 Vivipariajaninensis (MOUSSON). Dollfus, Bull. Soc. Gio!. Fr., 22 (4), p.123. Material examined: Numerous empty modern shells (see fig. 6.1 for sampling localities); fossil material from 284. Diagnosis: Shell large (mean height = 54.9mm, mean breadth = 40.1mm, n = 16), semi-transparent, broadly conical, olive green - brown in colour. Umbilicus absent. Spire tapers to a moderately pointed apex. Surface covered with growth-lines; three chestnut-brown bands visible on body whorl, two bands on the others. Sutures moderately deep and whorls convex. Whorls 5-6. Body whorl large, swollen, nearly 75% of the total shell height. Aperture large, ear-shaped,with rounded outer margin. Operculum has concentric structure, with distinct nucleus. FAUNA AND BIOSTRATIGRAPHY. 109 Occurrence: Ioannina is the type locality for V. janinensis (Mousson, 1859). It was also recorded by Dollfus (1922) as being abundant in the modem lake. Viviparids are widely distributed across nOlthem Europe, around the eastern Mediterranean, across central Africa, southern Asia, north and eastern Australia and central and eastern North America (Prashad, 1928). A large number of endemics have evolved, particularly in the Balkans (Prashad, 1928). V. janinensis is endemic to Ioannina and no records of it exist from elsewhere. Ecology: There are no published details on the ecology of V. janinensis. All of the specimens collected from the modern lake were shells recovered from the shore; no living specimens were observed. This suggests the preference of viviparids in general for offshore freshwater habitats in hard-water areas where the bedrock is dominated by carbonates (Macan, 1969; 0kland, 1990). Remarks: Reischtitz and Sattmann (1990) record V. contectus (MILLET, 1813) as Palt of the modern fauna of the lake. However, adult forms of V. contectus al'e much smaller than V janinensis, commonly 26-30mm high and 23-28mm broad (Graham, 1988). They also taper to a sharply pointed apex and have very deep sutures. It is easy, therefore, to see the similarity between adults of V. contectus and juveniles of V. janinensis. In view of the abundance of V. janinensis in Lake Pamvotis, it seems likely that this represents a mistaken identification by Reischtitz and Sattmann (1990). However, this can only be confilmed after examination of their collected material (al'chived in the Naturhistorischen Museum, Vienna). Family Valvatidae Genus Valvata MULLER, 1774 Valvata cristata MULLER, 1774 1774 Valvata cristata MULLER, Venn. Hist., ii, p.198. 1990 Valvata cristata MULLER. Reischiitz and Sattmann, Ann. Naturhist. Mus. Wien, 91B, p.256. Remarks: V. cristata has a distribution that ranges across most of Europe and parts of northern Asia, preferring freshwater habitats, such as lakes and slow-flowing rivers that al'e rich in aquatic vegetation (0kland, 1990). It WaS not found living in Lake Pamvotis by either Mousson (1859), Dollfus (1922), or during this study. FAUNA AND BIOSTRATIGRAPHY • 110 Valvata piscinalis (MULLER, 1774) 1774 Nerita piscinalis MULLER, Verm. Hist., ii, p.I72. 1859 Valvata piscinalis (MULLER). Mousson, Vierteljahrschr. Naturj Gesell. Ziirich, 4, p.55. Material examined: Numerous modern shells, both living and dead (see fig. 6.1 for sampling localities); fossil material from 284. Occurrence: V. piscinalis is common across most of Europe, as well as in western, central and northern Asia (0kland, 1990). The species is known from both modern and fossil sites in Greece (e.g. Schtitt, 1987; Sattmann and Reischtitz, 1988; Butot and Welter-Schultes, 1994). Ecology: Although V. piscinalis can be found in slow running waters and occasionally in small ponds, it has a distinct preference for lakes with abundant plant macrophytes (0k1and, 1990). This was confirmed at Ioannina, where live specimens were collected from shallow littoral areas with muddy substrates and abundant floating broadleaf macrophytes (sites 4 and 10, fig. 6.1) . Family Hydrobiidae Genus Mercuria (BOETERS, 1971) Mercuria confusa (FRAUENFELD, 1863) 1863 Amnicola confusa FRAUENFELD, Verhandl. k. k. zool. bot. Gesell. Wien, xiii, p.1029. 1863 Bythinia similis DRAPARNAUD, in Reeve and Reeve, Moll. Brit. Is ., p.188. 1859 Bythinia similis DRAPARNAUD. Mousson, Vierteljahrschr. Natufj Gesell. Ziirich, 4, p.54. Remarks: B. similis is a junior synonym of M. confusa. Mousson's (1859) record from Ioannina is here listed as such, but his specimens need checking to confirm this attribution. M. confusa is widespread around the Mediterranean and can be found in a variety of mildly brackish habitats with muddy substrates (Graham, 1988). It was not recorded by Dollfus (1922), Reischtitz and Sattmann (1990) or during this study. FAUNA AND BIOSTRATICRAPHY. III Family Bithyniidae Genus Bithynia LEACH in ABEL, 1818 Bithynia graeca (WESTERLUND, 1879) Plate Ill, figs. A-G 1859 Bythinia troscheli PAASCH, in Mousson, Vierteljahrschr. NatUlf Cesell. Zurich, 4, p.54. 1879 Bythinia graeca WESTERLUND, in Westerlund and Blanc, Aper. Faune Mal. Crece, p.l37. 1922 Bithynia boissieri KUSTER. Dollfus, Bull. Soc. Ciol. Fr., 22 (4) , p.123. 1990 Bithynia graeca (WESTERLUND) . Reischi.itz and Sattmann, Ann. Naturhist. Mus. Wien,91B, p.256 . Material examined: Occasional empty modern shells (all juvenile) (see fig. 6.1 for sampling localities); fossil material from 284, mostly juvenile. Diagnosis: Shell broadly conical, relatively slender, opaque, tapering to a pointed apex. Height approximately Ilmm, breadth approximately 6.5mm. Surface covered with faint growth lines. Sutures moderately deep, whorls convex. Whorls 5-6. Body whorl large, swollen, nearly 40% of the shell height. Aperture large, oval, with a reflected lip (plate Ill). Calcitic operculum has a concentric stlUcture, with a distinct paucispiral nucleus. Occurrence: loannina is the type locality for Bithynia graeca (Westerlund and Blanc, 1879). It has a distribution that extends across northern Greece and around the northern Aegean and Anatolian coastal areas (Schtitt, 1987). Ecology: Eleutheriadis et al. (1993) recently conducted a study of B. graeca from Lake Kerkini, an artificial lake in northern Greece. They noted that it prefers hard or medium waters and is most abundant at the barrage of the lake. During the summer it feeds on diatoms, algae and pond-weed, whereas during the winter it prefers to be buried in mud, feeding on organic detritus. Its apparent dislike for stagnant waters was reflected at loannina, where it was only found at the open sampling sites (e.g. sites 1, 8 and 10, fig. 6.1), rather than those in backwater areas. Remarks: Mousson (1859) described two species of bithyniid in the modern fauna at loannina. The smaller he called B. similis, which is not a tlUe bithyniid but a hydrobiid (Mercuria confusa, see above). He identified the larger species as B. troscheli PAASCH, 1842, which is a form closely related to B. leachii SHEPPARD, 1823 (a well-known and widespread European species) and regarded by some as conspecific. Dollfus (1922) also identified the modern bithyniid in Lake Pamvotis as a form of B. leachii , known as FAUNA AND BIOSTRATIGRAPHY • 112 B. boissieri KOSTER, 1852. Whilst B. leachii is very similar to the bithyniid found at Ioannina, it is commonly much smaller (approximately 5mm high and 4.5mm broad), has deeper sutures, a larger body whorl and is generally less slender (Graham, 1988). It is possible therefore, that Mousson (1859) and Dollfus (1922) only examined juvenile forms from Lake Pamvotis. Westerlund and Blanc (1879) considered that the bithyniid from Ioannina was sufficiently different from B. leachii to describe it a new species, B. graeca. This view was later supported by Schtitt (1987) in his discussion and review of Balkan bithyniids. Family Lyrnnaeidae Genus Lymnaea LAMARCK, 1799 Lymnaea auricularia (LINNAEUS, 1758) 1758 Helix auricularia LINNAEUS, Syst. Nat., ed.10, p.774, no.617 . 1922 Limnea auricularia (LINNAEUS) . Dollfus, Bull. Soc. Geol. Fr., 22 (4), p.123 . Material examined: Numerous modern shells, both living and dead (see fig . 6.1 for sampling localities); no fossil material was recovered from 284. Occurrence: L. auricularia is found throughout Europe, Asia, northern Africa and Alaska and has been introduced to the continental United States (0kland, 1990). It is widespread in Greece, where it is known from both modern and fossil records (e.g. Schtitt et al., 1985; Schtitt, 1987; Sattmann and Reischtitz, 1988; Butot and Welter­ Schultes, 1995). Ecology: L. auricularia generally prefers standing freshwater bodies, pruticularly lakes in hard-water areas (Macan, 1969; 0kland, 1990). At Ioannina, live specimens were particularly abundant at shallow, vegetation-rich littoral sites with muddy substrates (e.g. site 4, fig. 6.1). Remarks: Interestingly, L. auricularia was not recorded as part of the modern fauna by Mousson (1859) or Reischtitz and Sattmann (1990), although it was included by Dollfus (1922). FAUNA AND BIOSTRATICRAPHY. 113 Lymnaea peregra (MULLER, 1774) 1774 Buccinum peregrum MULLER, Verm. Hist. H, p.130. 1859 Limnaeus vulgaris (MULLER). Mousson, Vierteljahrschr. Natulf, Cesell. Zurich, 4, p.52. 1990 Lymnaea peregra (MULLER). Reischiitz and Sattmann, Ann. Naturhist. Mus. Wien, 91B , p.257 . Material examined: Occasional fossil material from 284. Occurrence: L. peregra is widespread throughout Europe, northern and middle Asia and north-western Africa (0kland, 1990). It is also well-known as a modern species from the Balkans, for example from Lake Prespa (Sattmann and Reischiitz,1988) and from the fossil record, for example the Lower Quaternary deposits of Greek Macedonia (Schiitt, 1987). Ecology: L. peregra prefers lakes and slow-flowing rivers rich in aquatic vegetation (0kland, 1990). No modern forms were found at Ioannina during this study, although since it has previously been recorded as patt of the modern fauna by Mousson (1859) and Reischiitz and Sattman (1990), it may be recovered with further detailed sampling. Lymnaea stagnalis (L1NNAEUS, 1758) 1758 Helix stagnalis LINNAEUS, Syst. Nat., ed.lO, p.774, no.612. 1859 Limnaeus stagnalis (LINNAEUS). Mousson, Vierteljahrschr. Nattllf, Cesell. Zurich, 4, p.52. 1922 Lil1lnea stagnalis (LINNAEUS). Dollfus, Bull. Soc. Cia/. Fr., 22 (4), p.123. Material examined: Numerous modern shells, both living and dead (see fig. 6.1 for sampling localities); no fossil material was recovered from 284. Occurrence: L. stagna lis has a holarctic distribution, being found throughout Europe, Asia, North America and parts of northern Africa. It is well known in Greece from both modern and fossil records (e.g. Schiitt et al., 1985; Schiitt, 1987; Sattmann and Reischiitz, 1988; Butot and Welter-Schultes, 1995). Ecology: L. stagnalis can be found in most freshwater habitiats, but has a preference for lakes in hard-water areas with abundant macrophytic vegetation (Macan, 1969; FAUNA AND BIOSTRATIGRAPHY • 114 0kland, 1990). This was confirmed at Ioannina, where live specimens were found to be abundant in shallow, vegetation-rich backwater sites (e.g. site 7, fig 6.1). Family Physidae Genus Physa DRAPARNAuD,1801 Physa acuta DRAPARNAUD, 1805 1805 Physa acuta DRAPARNAUD, Hist. Moll. France, p.55, pl.iii, figs. 10 and 11 Material examined: Several modern shells, both living and dead (see fig. 6.1 for sampling localities); no fossil material was recovered from 284. Occurrence: P. acuta is generally known as a Mediterranean species (Macan, 1969) and can be found throughout the Balkans, for example in Lake Kerkini in northern Greece (Eleutheriadis et al., 1993). It is also found in the fossil record from the region, for example in Lower Pleistocene deposits from north-eastern Greece (Schtitt, 1987). This is the first record of it from Ioannina. Ecology: P. acuta is known to favour marshy or vegetation-rich freshwater bodies, particularly lakes (Macan, 1969; Eleutheriadis et al., 1993). This was confirmed at Ioannina, where live specimens were abundant at site 4, a shallow littoral area with abundant broadleaf vegetation. Family Planorbidae Genus Planorbis GEOFFROY, 1767 Planorbis carinatus MULLER, 1774 1774 Planorbis carinatus MULLER, Verm. Hist., ii, p.157 . 1859 Planorbis carinatus MULLER. Mousson, Vierteljahrschr. Naturf Gesell. Ziirich, 4, p.53. 1922 Planorbis carinatus MULLER. Dollfus, Bull. Soc. Geol. Fr., 22 (4), p.123. Remarks: P. carinatus is common in a range of lakes rich in aquatic vegetation across most of Europe and parts of Asia (Meier-Brook, 1983; 0kland, 1990). Although recorded by Mousson (1859) and Dollfus (1922) as part of the modern fauna, it was not found by either Reischtitz and Sattmann (1990) or this study. FAUNA AND BIOSTRATlGRAPHY • 115 Planorbis planorbis (LINNAEUS, 1758) 1758 Helix planorbis LINNAEUS, Syst. Nat., ed.l0, p.769, no.578. 1805 Planorbis marginatus DRAPARNAUD, Hist. Moll. France, pA5, pl.ii, figs. 11 and 12. 1859 Planorbis marginatus DRAPARNAUD . Mousson, Vie!1eljahrschr. Nattllf Gesell. ZUrich, 4, p.53 . 1990 Planorbis planorbis (LINNAEUS). Reischiitz and Sattmann, Ann. Naturhist. Mus. Wien, 91B, p.257 . Remarks: P. planorbis is common in a range of lakes and ponds rich in aquatic vegetation across most of Europe, western and northern Asia and parts of North Africa (Meier-Brook, 1983; 0kland, 1990). Although recorded by Mousson (1859) and Reischtitz and Sattmann (1990) it was not found as part of the modern fauna by either Dollfus (1922) or this study. Genus Anisus STUDER, 1820 Anisus vorticulus (TROSCHEL, 1834) 1834 Planorbis vorticulus TROSCHEL, De Limnaeaceis, p.51. Material examined: Rare fossil material from 284. Occurrence: A. vorticulus has a distribution stretching across central and south-eastern Europe, into the western regions of Asia (Meier-Brook, 1983). This is the first record of this species from Ioannina. Ecology: A. vorticulus can be found in a variety of freshwater habitats, but like many of the more common planorbids, has a preference for lakes with abundant macrophytic vegetation (0kland, 1990). No modern material was found, making it impossible to assess its ecological preferences at Ioannina. FAUNA AND BIOSTRATIGRAPHY • 116 Genus Gyraulus CHARPENTIER, 1837 Gyraulus albus (MULLER, 1774) 1774 Planorbis albus MULLER, Verm. Hist. , ii, p.l64. Material examined: Occasional fossil material from 284. Occurrence: Gyraulus albus is known throughout Europe and in western parts of Asia (Meier-Brook, 1983). It is also recorded from numerous fossil and modern sites in Greece (e.g. Schtitt et al., 1985; Schtitt, 1987; Sattmann and Reischtitz, 1988). This is the first record of this species from Ioannina. Ecology: Found in most freshwater habitats, G. albus prefers lakes with abundant macrophytic vegetation (0kland, 1990). No modern material was found , making it impossible to assess its preferences at Ioannina. Gyraulus janinensis (MOUSSON, 1859) Plate Ill, figs. H-M 1859 Planorbis janinensis MOUSSON, Vierteljahrschr. NatUlf Gesell. ZUrich, 4, p.53. Material examined: Occasional empty modern shells (see fig. 6.1 for sampling localities); fossil material from 284. Diagnosis:, Shell discoidal, relatively small (mean breadth = 5mm, mean height = 1.7mm, n = 5), thin and semi-transparent. Weak traces of spiral sculpture, pruticularly on final whorl. Wide, depressed umbilicus. Spire is involute, with each whorl overlapping the previous one. Whorls 4-5, rapidly enlarging. Moderately deep sutures. Keel distinctive and blunt in comparison to G. albus. Ovate aperture. Occurrence: Ioannina is the type locality for G. janinensis. It is unknown elsewhere and appears to be endemic. Ecology: No ecological information IS available on G.· janinensis. It is likely, however, that in common with other similru' planorbids it prefers lake habitats rich in aquatic vegetation. It was found at a variety of sites at Ioannina (fig. 6.1), making it difficult to assess any specific ecological preferences. FAUNA AND BIOSTRATIGRAPHY. 117 Remarks: Endemic species of Gyraulus are well-known from the Balkans. For example, five endemic species have been recorded from Lakes Ohrid and Prespa (e.g. Hubendick and Radoman, 1959), although these have all now been assigned to the subgenus Carinogyraulus POLlNSKl, 1929 (Meier-Brook, 1983). The morphological characteristics of the form at Ioannina clearly permit a taxonomic revision, enabling it to be transferred from the genus Planorbis to Gyraulus. Genus Planorbarius FRORIEP, 1806 Planorbarius corneus (LINNAEUS, 1758) Plate 11, figs. D, H, I 1758 Helix cornea L1NNAEUS, Syst. Nat., ed.lO, p.770, no.587. 1859 Planorbis corneus (L1NNAEUS) . Mousson, Vierteljahrschr. Naturf Gesell. ZUrich, 4, p.52. 1922 Planorbis corneus (L1NNAEUS). Dollfus, Bull. Soc. Gi o/. Fr., 22 (4), p.123. Material examined: Numerous modern shells , both living and dead (see fig. 6.1 for sampling localities); no fossil material was recovered from 284. Occurrence: P. corneus is common throughout most of Europe (except the north), as well as large parts of Asia (0kland, 1990) and the Balkans (e.g. Stankovic, 1960). On the Greek mainland, it is widespread except in the Peleponnese, although it has been found in Pleistocene deposits from that region (Schtitt et al., 1985). It is also known from a range of Quaternary deposits from elsewhere in Greece (e.g. Schtitt, 1987). Ecology: P. corneus can be found in lakes and ponds, although it appears to favour smaller freshwater bodies rich in macrophytic vegetation (0kland, 1990). This was confirmed at Ioannina, where live specimens were abundant, particularly in vegetation­ rich backwater sites (e.g. sites 2, 6 and 7, see fig. 6.1). Remarks: The species of P. corneus found at Ioannina is unusually large (adults are commonly -40mm in diameter, compared with the -30mm diameter of more typical specimens). Schtitt (1987) also discusses similarly large specimens of P. corneus from north-eastern Greece and Lake Prespa. He suggests that they should strictly be referred to as Planorbarius corneus fOlma grandis DUNKER, 1850. FAUNA AND BIOSTRATIGRAPHY. 118 Family Ancylidae Genus Ancylus GEOFFROY, 1767 Ancylus fiuviatilis MULLER, 1774 1774 Ancylus fluviatilis MULLER, Venn. Hist ., ii, p.20l. 1859 Ancylus radio latus, KUSTER. Mousson, Vierteljahrschr. Natwf. Gesell. ZUrich, 4, p.54. 1990 Ancylus fluviatilis MULLER. Reischtitz and Sattmann, Ann. Naturhist. Mus. Wien, 91B, p.257. Material examined: A single juvenile shell from site 7 of the modern lake (see fig. 6 .1 for sampling locality). Occurrence: A. fluviatilis has a broad distribution throughout most of central and southern Europe (0kland, 1990). It is also well-known from Greece (e.g. Sattmann and Reischiitz, 1988). Ecology: A. fluviatilis has a preference for rapid-flowing rivers and lake environments subject to wave action. It also prefers habitats with stony substrates and minimal aquatic vegetation (0kland, 1990). Remarks: The single, juvenile shell examined possessed radial striations from the apex that were finer than normal for A. fluviatilis. It is possible therefore that it represents a species of Ferrissia WALKER, 1903, although without adult specimens, this is impossible to verify. Since A. fluviatilis has been recorded from Lake Pamvotis by both Mousson (1859) and Reischiitz and Sattmann (1990), this specimen has also been listed as such, pending further investigation. Class Bivalvia Family Unionidae Genus Anodonta (LINNAEUS, 1758) Anodonta anatina (LINNAEUS, 1758) 1758 Mytilus anatinus LlNNAEUS, Syst. Nat., ed. lO, p.706, no. 219. 1859 Anodonta piscinalis (NILSSON) . Mousson, Vierteljahrschr. Natwf. Gesell. ZUrich, 4, p.56. 1922 Anodonta anatina (LlNNAEUS). Dollfus, Bull. Soc. Gio!. Fr., 22 (4), p.123. FAUNA AND BIOSTRATIGRAPHY. 119 Material examined: Several dead shells from sampling site 2 of the modern lake (fig. 6.1). It was not present in the fossil fauna from 284. Occurrence: A. anatina has a broad palaearctic distribution (Ellis, 1962) and is known throughout the Balkans as part of the modern and fossil record (e.g. Butot and Welter­ Schultes, 1994). Ecology: A. anatina prefers freshwater habitats such as rivers, canals and lakes with sandy substrates in which it can bury itself (Ellis, 1962). At Ioannina it was only found at site 2 (fig. 6.1), a relatively shallow backwater area with a muddy substrate. It is probable that the dead shells were transported to this site and washed ashore by wave action. Anodonta cygnea (LINNAEUS, 1758) 1758 Mytilus cygneus LINNAEUS, Syst. Nat., ed.10, p.706, no. 218. 1859 Anodonta cellensis (LINNAEUS). Mousson, Vierteljahrschr. Natuif. Gesell. ZUrich, 4, p.56. Material examined: A single pair of dead shells from sampling site 1 of the modern lake (fig. 6.1). It was not present in the fossil fauna from 284. Occurrence: A. cygnea has a broad palaearctic distribution (Ellis, 1962). It is widespread throughout the Balkans and is also known from the Quaternaty fossil record from Greece (e.g. Schtitt, 1987). Ecology: A. cygnea prefers freshwater habitats such as rivers, canals and lakes with muddy substrates (Ellis, 1962). At Ioannina it was only found at site 1 (fig. 6.1), a relatively high energy beach where it is probable that it was washed up by wave-action. Family Dreissenidae Genus Dreissena BENEDEN, 1835 Subgenus Carinodreissena L'VOVA AND STAROBOGATOV, 1982 Dreissena (Carinodreissena) cf. stankovici L'VOVA AND STAROBOGATOV, 1982 Plate n, figs. E, F, J FAUNA AND BIOSTRATIGRAPHY. 120 1982 Dreissena (Carillodreissena) stankovici L ' VOVA AND STAROBOGATOV, Zoologicheskij Zhurnal, 61 (11), p.1749, fig .I. Material examined: Numerous dead shells from the modern lake shore (see fig . 6.1 for sampling locations); fossil material from 284; comparative modern material from Lake Ohrid (collected by T. Meijer). Occurrence: D. stankovici was originally described as an endemic species from Lake Ohrid (L'vova and Starobogatov, 1982). Ecology: Little is known concerning the ecology of D. stankovici, although Dreissena sp. is known to prefer shallow, relatively high energy littoral areas in a wide range of fresh and brackish conditions. It often occurs in mussel 'beds' in extremely high numbers, attached to the substrate by means of byssal threads. Remarks: Dreissena was recorded (as D. polymorpha PALLAS, 1771) as patt of the modern fauna at Ioannina by both Mousson (1859) and Dollfus (1922). D. polymorpha has a broad distribution as both a fossil and a modern form in western Europe, parts of Turkey, parts of western Asia (including the Caspian Sea, Aral Sea and the Black Sea) and the Balkans (e.g. Serafimova-Hadzische, 1974; Sattmann and Reischtitz, 1988; Schtitt, 1993; Rosenberg and Ludyanskiy, 1994). However, examination of the specimens from Ioannina by T. Meijer (RGD, Haat'lem) suggested that both the modern and fossil specimens were not D, polymorpha, since they had a thread-like carina, rather than the more usual blunt carina seen on D, polymorpha. He thought that the Ioannina specimens to be most similar to the endemic Ohrid species D. stankovici described by L'vova and Stat'obogatov (1982) (T. Meijer, pers comm.). These authors suggested assigning the Lake Ohrid species to a new subgenus, Carinodreissena, a recommendation adopted by Rosenberg and Ludyanskiy (1994) in their recent nomenclatural review of this genus. The Ioannina specimens are very similat' to the Ohrid material both in terms of overall morphology and the presence of a thread-like carina. They also possess a septum that is shaped like an equilateral triangle, rather than the more irregulat'ly-shaped triangulat' septum of D. polymorpha (L'vova and Starobogatov, 1982), However, the Ioannina forms are smaller and generally more slender, with an average length of approximately 23mm (n = 16), as opposed to an average length of 40mm for the Ohrid species (L'vova and Starobogatov, 1982). It is therefore possible that they represent a completely new species, perhaps endemic to the lake. Clearly, further comparison with type material is necessary before any final assessment can be made. FAUNA AND BIOSTRATIGRAPHY • 121 Family Pisidiidae Genus Pisidium PFEIFFER, 1821 Pisidium casertanum (POLl, 1791) 1791 Cardium casertanum POLl, Test. utr. Silicae, i, ord.II, p.65, pl.xvi, fig. 1. 1990 Pisidium caseltanum (POLl). Reischiitz and Sattmann, Ann. Naturhist. Mus. Wien, 91B, p.258 . Remarks: P. casertanum is a very widely distributed, eurytopic species. It can be found throughout Europe, parts of Asia, Africa, North America and New Zealand in various freshwater habitats at altitudes up to 2,500m and at depths down to 40m (Ellis, 1962). It was not found as part of the modern fauna by either Mousson (1859), Dollfus (1922) or this study. Pisidium nitidum JENYNS, 1832 1832 Pisidium nitidum JENYNS, TraIlS. Camb. Phi/' Soc., iv, p.304, p\.xx, figs. 7 and 8. Material examined: Numerous dead shells from the modern lake (see fig. 6.1 for sampling sites); fossil material from 284. Occurrence: P. nitidum is widespread throughout Europe and parts of North Amel1ca (Ellis, 1962). It is also well known from the fossil record, for example from Lower Pleistocene deposits in north-eastern Greece (Schiitt, 1987) and the Megalopolis Basin (Schiitt, 1985). This is the first record of P. nitidum from Ioannina. Ecology: P. nitidum can be found in most lakes, streams, rivers and ponds, though prefers harder water areas (Ellis, 1962). At Ioannina it was only found as dead shells around the lake edge (fig. 6.1), making more specific conclusions concerning its ecology there difficult. Pisidium spp. Material examined: Several dead shells from the shores of the modern lake (see fig. 6.1 for sampling sites); fossil material from 284. FAUNA AND BIOSTRATIGRAPHY. 122 Remarks: It is notoriously difficult to distinguish between the different species of Pisidium, especially with worn fossil specimens. Several species were found in both the modern and fossil fauna at Ioannina as part of this study, of which only P. nitidum was identified to species level (above) . No species of Pisidium were found by either Mousson (1859) or Dollfus (1922) in their studies of the modern lake fauna, although Reischiitz and Sattmann (1990) found P. casertanum (above). Specialist examination of both the modern and fossil fauna is clearly necessary. Genus Sphaerium SCOPOLI, 1777 Sphaerium corneum (LINNAEUS, 1758) 1758 Tellina cornea LINNAEUS, Syst. Nat., ed.lO, p.678, no.57. 1859 Cyclas cornea (LINNAEUS). Mousson, Vierteljahrschr. Natwf Gesell. ZUrich, 4, p.55. Remarks: According to Ellis (1962), S. corneum has a holarctic distribution throughout Europe, nOlthern Asia and parts of North America. It is also well known from the fossil record, for example from Lower Pleistocene deposits in north-eastern Greece (Schiitt, 1987) and the Megal6polis Basin (Schiitt, 1985). It lives up to depths of 30m in most kinds of fresh-water habitats and although can tolerate mildly brackish conditions, it cannot live in polluted water (Ellis, 1962). This may explain its absence from the modem faunallist of Dollfus (1922) and from this study. 6.2.2 Modern Aquatic Molluscan Fauna During September, 1994, water chemistry and sediment samples were taken at eleven littoral zone sites around Lake Pamvotis (section 3.2.6). At the same time, a qualitative collection of molluscs was made at eight of these sites. The sample site locations are shown in fig 6.1 and briefly described in appendix A. A total of 14 taxa were collected: Viviparus janinensis Valvata piscinalis Bithynia graeca Lymnaea auricularia Lymnaea stagnalis Physaacuta Gyraulus janinensis Gyraulus albus Planorbarius corneus Anodonta cygnea Anodonta anatina Dreissena cf. stankovici . Pisidium nitidum Pisidium spp. FAUNA AND BJOSTRATIGRAPHY. 123 It must be emphasised that the collection techniques employed were neither rigorous nor quantitative and the list is likely to be incomplete (see table 6.1 for comparisons with other modern faunal studies). Nevertheless, this list of taxa is of value since there are several differences to those published previously, in particular, the study by Mousson (1859). This could be a reflection of the onset of serious pollution problems, a response to the attificial draining of the lake at the end of the last century, or a combination of the two. Certainly, these are likely to be the two most impOltant factors affecting the lake ecology over such a short period of time. Although collection of the modern fauna was not undertaken in a quantitative manner, certain interesting patterns do emerge which help to confirm what is known of the ecological preferences of certain species. For example, Dreissena was only collected from site 1 on the south-western shore, where it dominated the mollusc an fauna. This is a shallow-shelving beach subject to relatively high-energy conditions due to the prevailing winds. In fact, although not formally sampled, Dreissena could be found as dead shell accumulations at several other beach sites along this stretch of lake edge. Dreissena is known to occur in abundance in shallow, littoral environments that experience reasonably high-energy conditions. All of the other sampling sites provided, by comparison, relatively low-energy habitats. This is an impOltant ecological observation; a similar concentration of Dreissena in the fossil record can also be interpreted as representing a shallow, littoral environment. The mollusc an fauna from site 1 also included a wide range of other species, several of which are not regarded as littoral. This is unsurprising; prevailing winds will generate sufficient wave activity to carry most shells (whether derived from shallow or deep waters) and deposit them on the beach. Site 4 represents a low-energy environment with a muddy substrate and abundant aquatic vegetation. This is a habitat suited to such species as Lymnaea auricularia, L. stagnalis and Physa acuta, all of which at'e found here. Similat· environments at'e represented at site 7 (where L. stagnalis is found) and site 2 (where L. auricularia is found). At site 11, a steep-sided vegetation-free channel cut for irrigation purposes, only deeper water species such as Viviparus janinensis and Planorbarius corneus can be found. Observations of a similar nature can be made at other sampling sites. FAUNA AND BIOSTRATIGRAPHY. 124 6.2.3 Fossil Aquatic Molluscan Fauna Molluscan faunal remains were preserved in core 284 down to a depth of about 145m. Throughout most of this interval, preservation was relatively poor, with only fragments and opercula being recovered. Nine species were identified: Viviparus janinensis Valvata piscinalis Bithynia graeca Lymnaea peregra Anisus vorticulus Gyraulus albus Gyraulus janinensis Dreissena cf. stankovici Pisidium nitidum Pisidium spp. The well-established quantitative method for carrying out mollusc an analysis (counting the number of apices from a set weight of sediment) was of little use here, mainly because of the small amount of sediment available from each level and the low faunal abundances. Of the species listed above, the most common were Valvata piscinalis, Viviparus janinensis, Bithynia graeca and Dreissena cf. stankovici; the others were only found sporadically. Fragments of these molluscs (and bithyniid opercula) were found intermittently throughout the top -145m of the core. Unfortunately, the counts of picked specimens were too low to permit a statistically valid assessment of the faunal structure. Nevertheless, the data still allow a few general observations to be made. In general, the occurrence together of the four main species listed above would suggest a shallow littoral environment, somewhat like sample site 1 today. Although Viviparus and Bithynia in particular prefer non-littoral habitats, their remains would still be found in high-energy littoral environments (much as they are today). In these cases, Dreissena would be the dominant species; the others would be found in association with it, but only in relatively small numbers. The presence of densely packed Dreissena beds in the core therefore suggests a true littoral, shallow water environment. This situation is seen at occasional discrete intervals in the core, illustrated in fig. 6.2 and described below. Elsewhere, Dreissena is either absent or a minor constituent of the fauna, suggesting a deeper water/lower energy environment. The first consistent record of mollusc fragments (dominantly Bithynia and Valvata) occurs at a depth of around 145m. They are seen occasionally in the core material until around 125m, at which point they disappear. Fragments again occur above about 85m, although initially these are rare. From 70m, they become more common until between approximately 45-42m several discrete Dreissena beds occur. Above these, the sediment returns to being only occasionally shelly until further Dreissena beds are seen FAUNA AND BIOSTRATIGRAPHY • 125 0 5 10 15 20 25 30 35 40 45 50 55 60 65 70 § 75 ..c: 0. <1.l 80 Cl 85 90 95 100 105 110 115 120 125 130 135 140 i45 150 0 10 20 30 40 50 s D Carbonate Content (%) Fig. 6.2 Relative lake-level inferred from the frequency of aquatic molluscs (solid/dashed line). S = shallower; D = deeper; .,!;. = location of Dreissena beds (see text for details). FAUNA AND BIOSTRATIGRAPHY • 126 at approximately 32m and 26.3m. Occasional fragments are then seen until around 18.5m, after which they become more common. Between 8.5-7.5m, the lithology becomes more clay-rich (see section 4.1.1) and contains many tiny fragments, of which most are bithyniid opercula. After 7.5m, the lithology becomes a shelly silt once again, with abundant fragments of Bithynia, Valvata, Dreissena and, towards the very top of the sequence, Gyraulus janinensis, Anisus vorticulus and Pisidium spp .. The occurrence of mollusc an fauna described above clearly has implications for interpreting such factors as long-term lake-level fluctuations over time. This is discussed further in section 7.3.1. The low counts and lack of detail in the fossil assemblages means that the molluscan fauna is unsatisfactory for any biostratigraphical purposes. 6.2.4 Aquatic Molluscan Fauna from Core 256 Although this study did not consider in any detail the molluscan fauna of core 256 (the marginal core drilled to the south-west of 284), a few pilot investigations of the lower section were initially undertaken. This lower part of 256 is thought to be older than any of 284, since all the sediments have a reversed palaeomagnetic signature (unpubl. data). In addition, this is the section of core that reaches bedrock and might therefore be Plio­ Pleistocene in age (the age of the lake is thought to be Plio-Pleistocene - see section 2.3). Four aquatic species were recovered, all of which are known from Upper Pliocene lacustrine deposits sampled from the Katsikas site described above (Dollfus, 1922; Aubouin, 1959; Gillet, 1963; Guernet et al., 1977). The species recovered from 256 are listed in table 6.3, along with other taxa known from the Katsikas site. Without further detailed investigation, it is not yet possible to make a robust biostratigraphical correlation between these deposits and the lower patt of 256. Species Viviparus clathrata (DESHA YEs) Viviparus brusinai (NEUMA YR) Viviparus megarensis (FUCHS), Theodoxus micans (GAUDRY AND FISCHER) Theodoxus licherdopoli STEFANESCU Theodoxus quadrifasciatus (BIELZ) Pyrgula brusinai TOURNOUER Pyrgula eugeniae (BERNADI) Melanopsis costata (OLIVIER) Melania curvicosta DESHA YES Melania rhodensis BUKOWSKI Neumayria janinensis (DOLLFUS) Bithynia cf. meridionalis (FRAUENFELD) Ancylus sp. Valvata sp. DolIfus (1922) + + + + + + + Aubouin GilIet Guernet et al. (1959) (1963) (1977) + + + + + + + + + + +2 + + + + + + + + + + ?3 + + + Table 6.3 Comparison of aquatic molluscan fauna recovered from Upper Pliocene deposits at Katsikas with those recovered from core 256. , Viviparus megarensis may be a synonym of Viviparus brusinai. 256 (this study) + + + + + 2 Description of Pyrgula sp. by Guernet et al. (1977) matches that of Pyrgula brusinai. Their material must be exanllned before a critical assessment can be made. 3 Guernet et al. (1977) refer to Hydrobia janinensis (DOLLFUS). It is possible that they actually mean Neumayria janinensis (DOLLFUS). Again, their material must be examined before a critical assessment can be made ~ c::: ~ ~ § ttl ...... a ~ ~ ~ :::l Cl :::>::l ~ ~ '""<: • ...... N -.l FAUNA AND BIOSTRATlGRAPHY. 128 6.3 OSTRACOD FAUNA The ostracod faunas from selected parts of the loaninna record were examined as part of this study. In particular, assemblages from the Eemian and last glacial - Holocene intervals were analysed, along with modem material collected during September, 1992. These are discussed in detail below. Whilst there exist many broad studies of both modem and fossil ostracods from Greece (e.g. Griffiths, 1995a,b), there are very few studies of the ostracod fauna from loannina itself. Aubouin (1959) records the presence of Candona sp. at the Katsikas site. Guernet et al. (1977) also identify several ostracods from this site: Darwinula stevensoni, Candona stupelji, llyocypris bradyi and Cyprinotus sp. (now known as Heterocypris sp., see note below) . They also formally describe a new sub-species of Cyprideis torosa, as C. torosa janinensis. The present study represents the first detailed account of Quaternary and modem ostracod faunas from loannina. 6.3.1 Taxonomy As with molluscs, there are certain taxonomic problems inherent in working on ostracods from the Balkans. These include the high degree of endemism encountered with some genera (e.g. Candona, llyocypris, Leptocythere), as well as the difficulty in untangling the often unclear and complex stratigraphical schemes used by some of the Croatian, Slovenian, Yugoslavian and Greek authors (Yugoslavia is taken to include both Serbia and Montenegro). Fortunately, this task has been made considerably easier by Griffiths's (1995a) comprehensive database of European freshwater ostracods, in addition to his "biostratigraphic and palaeobiogeographic primer" (Griffiths, 1995b). His taxonomic conventions (also outlined in Griffiths and Evans, 1995) are used throughout this study. Before an account is given of the modem and fossil ostracod fauna found at loannina, special consideration needs to be given to the genus Candona, which has specific taxonomic problems. Candona s.l. BAIRD, 1845 is one of the broadest and most confusing of all European ostracod genera (Griffiths, 1995b). Griffiths (1995a) reports that although Limnofauna Europaea records over 150 extant species (LOffler and Danielopol, 1978), many more have since been described from a wide range of habitats (including subterranean and interstitial environments). Candona s.l. is a hugely speciose group, having a broad 1 FAUNA AND BIOSTRATIGRAPHY. 129 geographical distribution across most continents. Subtle differences in shell morphology, polymorphism and, occasionally, sexual dimorphism, widespread endemism and poor descriptions have given rise to much taxonomic confusion both with extant forms and the vast number of fossil species known since the Tertiary. Candona s.l. has long been in need of a comprehensive taxonomic revision and several schemes have been proposed. Probably the most widely accepted of these was suggested by Danielopol (1978), in which Candona s.s. is nominated as one of six new genera. For a comprehensive discussion regarding the 'Candona problem', see Griffiths (1995a). Unfortunately, despite applying the nomenclature of Danielopol (1978), many taxonomic problems remain within Candona s. s.. Petkovski (l969a,b) suggested splitting the genus into two broad groups, the 'neglectoids' and the 'candidoids' . However, the number of endemics and extinct species (particularly amongst the neglectoids) means that this classification is of little use except as a first order taxonomic distinction. In the Balkans for example, highly diverse endemic faunas are known from Lake Ohrid (e.g. Mikulic, 1961; Petkovski, 1969a), Lake Prespa (e.g. Petkovski, 1960), Lake Skadar (Petkovski, 1961) and the Pannonian Basin (e.g. Krstic, 1988). In Greece, C. neglecta s.s. and associated neglectoids are recorded at several modem and Quaternary sites, such as the Megal6polis Basin (Hiltermann and Ltittig, 1969), Patras (Femandez-Gonzalez et al., 1994), Limni Lema (Zangger and Malz, 1989) and Ioannina (Guemet et al. , 1977). The neglectoid forms found at Ioannina as part of this study are discussed in more detail below. 6.3.2 Systematic Review of the Ostracod Fauna from Ioannina A general description of the fourteen modem and fossil ostracod taxa found at Ioannina is now given. Their taxonomy is summarised, along with what is known of their occurrence, ecology and any other relevant details. As with the molluscs, the original citation is given for each species, followed by a synonymy that refers only to usage in relation to material from Ioannina. In considering distribution, emphasis is placed on European (and in particular, Balkan) occurrences. The ecological information is summarised in table 6.4. This is followed by separate consideration of the modem, last glacial - Holocene and Eemian assemblages and, where appropriate, an assessment made of their biostratigraphical and palaeoenvironmental importance. For the sake of clarity, distinction is made between those fossil species occurring in the Eemian, the last glacial- interglacial transition (LGIT, here taken to be the period from the height of the last glacial to the beginning of the Holocene) and the Holocene itself. Species DarwinuLa stevensoni (BRADY AND ROBERTSON, 1870) Cyprideis torosa (JONES, I 850) Leptocythere cf. ostrovskensis PETKOVSKl AND KEYSER, 1992 ParaLimnocythere cf. compressa (BRADY AND NORMAN, 1889) Ilyocypris bradyi SARS, 1890 Ilyocypris sLavonica SOKAC AND VAN HARTEN, 1978 Candona cf. dedeLica PETKOVSKl, 1969 Candona permanenta KRSTIC, 1985 Candona cf. parvuLa MIKULlC, 196 I Cypria ophtaLmica JURlNE, 1820 Cypridopsis vidua MULLER, 1776 Eucypris virens (JURI NE, 1820) Heterocypris rotundatus (BRONSHTEIN, 1928) Prionocypris sp. Habitat A eurytopic and eurythermal species. Commonly found in permanent lakes and ponds, no deeper than 10m. Prefers soft, muddy, plant-rich substrates. A eurytopic and euryhaline species. Capable of tolerating a wide range of salinities. Can be found in lagoons, deltas, estuaries and oligosaline lakes . Prefers a muddy or sandy substrate. Found no deeper than about 30m. I Little ecological information. Likely to prefer habitats with silty substrates and abundant macrophytic vegetation. Little ecological information. Likely to be a cold water stenothermal species. A littoral species that prefers muddy substrates and abundant vegetation. Prefers muddy and silty substrates in still or moving freshwater with abundant macrophytic vegetation. Little ecological information. Likely to be eurytopic, eurythermal and euryhaline, preferring benthic, sublittoral habitats with muddy or sandy substrates that are rich in decaying organic matter. No ecological information. Likely to be as for C. cf. dedeLica (above). Little ecological information. A benthic, sublittoral species, it probably prefers muddy or sandy substrates that are rich in decaying organic matter. A hardy, eurytopic species found in permanent and temporary water bodies. An active swimmer, it is often associated with submerged vegetation, especially reed beds . Generally found in the littoral zone of lakes and ponds. Often associated with algal mats and aquatic vegetation. Intolerant of low oxygen levels . Found in ephemeral habitats, including seasonally-flooded reed beds on lake margins. Also associated with well-vegetated shallow down-stream areas. Little ecological information. Likely to be a hardy, euryhaline species. Little ecological information. Likely to be a littoral cold water species, preferring muddy substrates and abundant aquatic vegetation. Occurrence in 284 M/H ILGH/E M H/LGH/E H M/H MI H/LGH M/H M/H/LGH/E LG/E M/H/LGH/E M/H H H LGH Table 6.4 List of ostracod fauna found during this study, with summarised ecological infonnation. M = modern; H = Holocene; LGH = Last glacial - Holocene; E = Eemian. ~ c:::: ~ ~ ~ O:l ..... <:::) V:l ;;5 ~ :::l Cl ~ "'tl ::r:: '"<: • VJ o FAUNA AND BIOSTRATIGRAPHY. 131 Site 6 Candona permanenta Cypria ophtalmica Site 1 Cyprideis torosa /lyocypris slavonica Candona pemzanenta Site 10 Darwinula stevensoni /lyocypris bradyi Candona dedelica Cypria ophtalmica Site 7 Candona pemzanenta Cypria ophtalmica Cypridopsis vidua Site 2 Candona pemzanenta ~. <,> J",>, eyp,'a aphtalmica ···:::t.\ 11 ." Lake Pamvotis Site 4 '., Site 11 Darwinula stevensoni Candona dedelica Candona pemzanenta Cypria ophtalmica Cypridopsis vidua Site 8 Darwinula stevensoni /lyocypris bradyi Candona permanenta Cypria ophtalmica Cypridopsis vidua Candona permal/el/ta Fig. 6.3 Sampling sites for modern ostracod fauna. See text for details . FAUNA AND BIOSTRATIGRAPHY • 132 Class Ostracoda Sub-class Podocopa Superfamily Darwinuloidea Family Darwinulidae Genus Darwinula BRADY AND ROBERTSON, 1885 Darwinula stevensoni (BRADY AND ROBERTSON, 1870) Plate VII, fig. F 1870 Polycheles stevensoni BRADY AND ROBERTSON, Ann. Mag. N.H., Series 4, VI, p.25 , pl.YI, figs . 1-7 and pl.X, figs. 4-14. 1977 Darwinula stevensoni (BRADY AND ROBERTSON, 1870). Guernet et al., Geobios, 10 (2), p.299 . Material examined: Modem valves and carapaces (see fig. 6.3 for sampling localities); fossil material from the Eemian, LGIT and Holocene intervals of 284. Occurrence: Darwinula stevensoni has a cosmopolitan distribution, being recorded from every continent except Australasia and Antarctica. In Europe, it is found south of latitude 600 N (Griffiths and Butlin, 1994). There are several Plio-Pleistocene records from the Balkans, including Greece (e.g. Hiltermann and Ltittig, 1969). D. stevensoni has also been reported from Upper Pliocene deposits at Ioannina (Guernet, et al., 1977). Ecology: Generally, D. stevensoni is both eurytopic and eurythermal and is usually found no deeper than about lOm in non-desiccating habitats, such as lakes and ponds (McGregor, 1969). Regarded primarily as a littoral species, it is thought to prefer soft, muddy, plant-rich substrates. Temperature is not generally limiting, as demonstrated by latitudinal and depth distributions. A comprehensive biological and ecological review can be found in Griffiths and Butlin (1994). Superfamily Cytheroidea Family Cytherideidae Genus Cyprideis JONES, 1857 Cyprideis torosa (JONES, 1850) Plate IV, figs. A-E FAUNA AND BIOSTRATIGRAPHY • 133 1850 Candona torosa JONES , 1850, Ann. Mag. N.H. , Series 2, VI, p.27, p1.3 , figs . 6a-e. 1977 Cyprideis torosa (lONES , 1850). Guernet et al., Geobios, 10 (2), p.301, pl.l, figs. 7-14. Material examined: Modern valves and carapaces from sampling site 1 (fig. 6.3). Occurrence: C. torosa is widespread throughout northern Europe, central Asia, central Africa and Mediterranean regions (Athersuch et ai., 1989). There are several Plio­ Pleistocene records from Greece (e.g. Mostafawi, 1986, 1994; Rommelt-Doll, 1990). Ecology: C. torosa is a eWhaline and eurytopic species that can tolerate salinities from almost freshwater to around 60%0. It can therefore be found inhabiting marginal marine environments such as lagoons, estuaries, fjords and deltas, as well as inland ponds and lakes. According to Athersuch et al. (1989), it prefers a muddy or sandy substrate and can be found at all depths down to about 30m. Remarks: The possible relationship between the carapace morphology of C. torosa and salinity levels has been much debated (e.g. Kilenyi, 1972; van Harten, 1975). A weak relationship between low salinity and the presence of tubercles on the valves has been suggested. However, some authors attribute the noding to other environmental parameters, such as the open or closed status of the water body (e.g. Bodergat et aI. , 1991), whilst others explain it as an expression of genetic polymorphism (e.g. Kilenyi, 1972). Clearly, further work is necessary to resolve the problem. Both noded and smooth forms of C. torosa were found in the modern sediment samples collected from Ioannina. Some carapaces were found with soft parts still intact; it is therefore clear that C. torosa is living in the lake today. No fossil specimens were found in the core material, indicating that its arrival and expansion in the lake has been very recent. It is possible that its success is related to pollution of the lake from agricultural and industrial waste during historical times, although few studies have been carried out on the effects that pollutants have on ostracod ecology. C. torosa dominated the fauna recovered from site 1, a beach to the north of the city, suggesting that it prefers higher-energy environments, with a sandy substrate. It is not clear whether the species of C. torosa occurring at Ioannina today is the same as the Upper Pliocene sub-species C. torosa janinensis described by Guernet et al. (1977). Comparison with the type material is necessary (the published description and plates illustrating this sub-species are of insufficient detail to permit a satisfactory assessment). FAUNA AND BIOSTRATIGRAPHY. 134 Family Leptocytheridae Genus Leptocythere SARS, 1926 Leptocythere cf. ostrovskensis PETKOVSKl AND KEYSER, 1992 Plate VI, figs. A-C 1992 Leptocythere ostrovskensis PETKOVSKI AND KEYSER, Mitt. hamb. zoo!. Mus. Inst., 89, p.228, pl.l, figs. 1-4. Material examined: Valves and carapaces from the Eemian, LGIT and Holocene intervals of 284. Occurrence: Extant freshwater leptocytherids are represented by only six species, all of them endemics from the Balkans. Three species were described from Lake Oill'id (Klie, 1939), two from Lake Prespa (Petkovski, 1959) and one from Lake Vegoritis in NW Greece (Petkovski and Keyser, 1992). Some fossil records exist (also from the Balkans), for example from the Upper Pliocene of the Mega16polis basin in Greece (Hiltermann and Llittig, 1969). The form occurring at Ioannina is possibly an undescribed endemic species of leptocytherid having the closest affinities with L. ostrovskensis, originally described from Lake Vegoritis (Petkovski and Keyser, 1992). Examination of the type-material is clearly necessary to enable critical comparisons. Ecology: No ecological infOlmation has been published on any of the freshwater leptocytherids:' In the Ioannina record it is found with Candona permanenta, /lyocypris slavonica, and Prionocypris, suggesting that it prefers habitats that have silty substrates and abundant macrophytic vegetation. Family Lirnnocytheridae Genus Paralimnocythere CARBONNEL, 1965 Paralimnocythere compressa (BRADY AND NORMAN, 1889) Plate VII, fig. C 1889 Limnicythere inopinata var. compressa BRADY AND NORMAN, Sci. Trans. Roy. Dub!. Soc., Series 2,4, p.170, pI. XVII, figs. 18-19. Material examined: Rare valves from the Holocene of 284 . . FAUNA AND BIOSTRATIGRAPHY. 135 Occurrence: P. compressa has a broad distribution across Europe in a wide variety of Quaternary deposits. It has not been collected alive since the nineteenth century (Martens, 1992). It has an extensive fossil record from the Balkans, being recorded from Croatia (e.g. Sokac, 1976) and Yugoslavia (e.g. Krstic, 1988). There are no other records from Greece. Ecology: The absence of modem material means that the ecology of P. compressa is unknown (Martens, 1992). Griffiths (l995a) suggests that it may be able to survive in seasonal habitats and is probably a cold water stenothermal species. Superfamily Cypridoidea Family Ilyocyprididae Genus /lyocypris BRADY AND NORMAN, 1889 Ilyocypris bradyi SARS, 1890 Plate IV, fig. F 1890 /lyocypris bradyi SARS, Christiana Vid. Selsk. Forh., p.59. 1977 /lyocypris bradyi SARS. Guernet et aI. , Geobios, 10 (2), p.301, pl.I , fig . IS. Material examined: Modem valves (see fig. 6.3 for sampling localities); fossil material from the Holocene interval of 284. Occurrence: Laffler and Danielopol (1978) record that l. bradyi is recorded throughout Europe, except in the northern Balkans and the Crimea. It is also known from North America (e.g. DelOlme, 1991). l. bradyi has a comprehensive Quaternary fossil record from across Europe (e.g. Griffiths, 1995a,b), including a Holocene record from southern Greece (Zangger and Malz, 1989). Ecology: Despite its broad distribution, there have been few detailed studies on the ecology of I. bradyi. It is thought to be associated with the littoral zone of lakes, as well as with springs. At Ioannina, l. bradyi was found in abundance at site 4 (fig. 6.3), a shallow littoral area of the lake with a muddy substrate and abundant floating and submerged aquatic vegetation. Remarks: Many ilyocyprid species are polymorphic, which along with a high degree of endemism, can make identification of fossil material extemely difficult (modem identification is based on genital characteristics). FAUNA AND BIOSTRATIGRAPHY • 136 Jlyocypris slavonica SOKAC AND VAN HARTEN, 1978 Plate IV, figs. G-H 1978 /lyocypris slavonica SOKAC AND VAN HARTEN, Geol. vjesnik, 30, p.219, pI. 1 and 2. Material examined: Modem valves (see fig. 6.3 for sampling localities); fossil material from the LGIT and Eemian intervals of 284. Occurrence: Until now, l. slavonica has only been known from the fossil record. It has been recorded from the Pleistocene of Croatia (e.g. Sokac, 1976; Sokac and van Harten, 1978), the Pleistocene of Yugoslavia (e.g. Krstic, 1985) and the Lower Pleistocene of Tegelen, in the Netherlands (Sokac and van Harten, 1978). This is the first recorded modern occurrence of the species. Ecology: Little is known of the ecology of l. slavonica. The Dutch and Croatian material (Sokac and van Harten, 1978) was found in sediments interpreted as being silty or muddy channel fills. Morphologically, 1. slavonica is most similar to Ilyocypris monstrifica (NORMAN, 1862), which occurs throughout north-western Europe. This is a warm-stenothermal flow-tolerant species that lives amongst submerged vegetation on muddy substrates. In the absence of other information, it would seem likely that I. slavonica has similar ecological preferences. Family Candonidae Genus Candona BAIRD, 1845 Candona cf. dedelica PETKOVSKI, 1969 Plate V, figs. E-F 1969 Candona dedelica PETKOVSKI, Acta Musei Macedonici Scientiarum Naturalhun, 11 (5), p.85 , figs . 6-9 and 14-17. Material examined: Modem valves (see fig. 6.3 for sampling localities); fossil material from the Holocene interval of 284. Occurrence: First described by Petkovski (1969a) from the Lake Ohrid, C. dedelica has also been described from the fossil record (Middle Pleistocene?) as C. cf. dedelica from the Milijevo Valley, near Beograd in Serbia (Krstic, et al., 1981). There are no other records from Greece. FAUNA AND BIOSTRATlGRAPHY. 137 Ecology: Not surprisingly, there is very little infOlmation on the ecology of C. dedelica. As a typical neglectoid (see above), it is likely to be epibenthic, moving around on and just within the sediment surface, feeding on decaying organic material (Griffiths, 1995a). It is probably eurytopic, able to withstand a broad range of temperatures and salinities. A few valves were found in the modem sediment samples from Ioannina, from sites 10 and 11 (fig. 6.3). Site 10, located south-east of Ioannina itself, was a shallow littoral site with a muddy substrate and abundant aquatic vegetation. Site 11 was a drainage channel at the eastem extent of the lake cut through the reed beds to a pumping station (for agricultural irrigation purposes). It had steep, muddy sides, some floating aquatic vegetation and the water had a distinct algal covenng. Candona permanenta KRSTIC, 1985 Plate V, figs. A-D 1985 Candona permanenta KRSTIC, Radovi Geoillstituta, 18, p.197, p\.1, figs. 1-3. Material examined: Modem valves and carapaces (see fig. 6.3 for sampling localities); fossil material from the Eemian, LGIT and Holocene intervals of 284. Occurrence: C. permanenta was first described by Krstic (1985) from Lower-Middle Pleistocene deposits at Vojvodina in the Pannonian Basin, Yugoslavia. It has since been recorded from other Lower and Middle Pleistocene deposits from the same basin (e.g. Krstic, 1993; Krstic and Schomikov, 1993). This is the first record from Greece and the only modem record of this species. Ecology: No ecological data exist for C. permanenta. As a typical neglectoid, the same ecological assumptions can be made as for C. dedelica. C. permanenta was found at Ioannina throughout core 284. Modem sediment samples (from almost all sampling sites) yielded carapaces with decaying soft parts, making it highly likely that C. permanenta lives in the lake today. Remarks: In their study of the Upper Pliocene fauna from the Katsikas site, Guemet et al. (1977) note the occurrence of Candona stupelji KRSTIC, 1974. First described from the village of Stupelj in Slovenia (Krstic, 1974), this form has remarkable morphological similarities with C. permanenta. It is possible that Guemet et al. (1977) FAUNA AND BIOSTRATIGRAPHY. 138 rnis-identified their species, but this IS impossible to ascertain without critical comparison of material. Candona cf. parvula MIKULIC, 1961 Plate V, figs . G-H 1961 Candona parvula MIKULIC, Bulletin du Museum d'Histoire Naturelle de Belgrade, B17 , p .98 , pl.1 , fig . lO. Material examined: Fossil material from the Eemian and LGIT intervals of 284. Occurrence: C. parvula was first described as an endemic species from Lake Ohrid by Mikulic (1961). Morphological similarities suggest that the Ioannina form is synonymous with C. parvula, although as the published descriptions and illustrations are poor, this can only be critical assessed by comparison with the type material. Ecology: Little is known of the ecology of C. parvula. Stankovic (1960) reports that it is a sublittoral benthic species, with a very limited distribution in littoral and profundal habitats. As a neglectoid, it is assumed that it also requires the presence of decaying organic matter within the substrate, on which it feeds. Remarks: C. cf. parvula abruptly disappears from the record in core 284 at a depth of 23 .99m (the significance of which is discussed below). Genus Cypria (ZENKER, 1854) Cypria ophtalmica JURINE, 1820 Plate VII, fig. E 1820 Monoculus ophtalmicus JURINE, Hist. Mon ., p.l78 , p1.19, figs. 16-17. Material examined: Modem valves and carapaces (see fig. 6.3 for sampling localities); fossil material from the Eemian, LGIT and Holocene intervals of 284. Occurrence: Sometimes also referred to as C. ophthalmica, this species is known from a wide variety of sites and is common in north-western Europe (e.g. Devoto, 1965; FAUNA AND BJOSTRATIGRAPHY. 139 Henderson, 1990) and in the Balkans (e.g. Krstic, 1988). Griffiths (1995a) notes that its relatively uncommon occurrence in Quaternary deposits is probably due to its avoidance of flowing waters and to the fragility of the shell. Ecology: C. ophtalmica occupies a wide range of freshwater habitats and is often regarded either as a pioneer species or an indicator of stressed environmental conditions, when present in a restricted fauna with other hardy species (Griffiths, 1995a). It is able to tolerate a wide range of variation in pH, temperature, anoxia and salinity (e.g. Delorme, 1991), is found in both permanent and temporary water bodies and is often associated with submerged vegetation (particularly reed beds). It is an active swimmer, but is also capable of burrowing into soft, muddy substrates (Griffiths and Martin, 1993). Family Cyprididae Genus Cypridopsis BRADY, 1867 Cypridopsis vidua (MULLER, 1776) Plate VII, figs. A-B 1776 Cypris vidua MULLER, Z. Dan. Prod., p.199 Material examined: Modem valves and carapaces (see fig. 6.3 for sampling localities); fossil material from the Holocene interval of 284. Occurrence: C. vidua is a very common species with a wide distribution across Europe and the Balkans in a variety of Quaternary deposits (although curiously no record exists from Greece) . Ecology: Griffiths (1995a) notes that C. vidua has an apparent preference for the littoral zone of eutrophic lakes and ponds. An active swimmer, it is also capable of burrowing in soft substrates. C. vidua is often associated with algal mats and aquatic vegetation such as Potamogeton (Tabacchi and Matmonier, 1994). It is also known to be intolerant of low oxygen levels (Danielopol, 1991). FAUNA AND BIOSTRATIGRAPHY • 140 Genus Eucypris (vAvRA,1891) Eucypris virens (JURINE, 1820) Plate VII, fig. D 1820 Monoculus virens, JURINE, Hist. Mon., p.174, pU8, figs. 15-16. Material examined: Rare fossil material from the Holocene interval of 284. Occurrence: E. virens is found throughout most of Europe and has a comprehensive Quaternary record (e.g. Laffler and Danielopol, 1978; Griffiths, 1995a,b). The only known record from Greece is a Lower Pleistocene sub-species, E. virens latissima ALM, 1914, from the Mega16polis Basin (Hiltermann and Ltittig, 1969). Ecology: Griffiths (1995a) notes that E. virens tends to occur in ephemeral habitats, including seasonally-flooded Phragmites reed beds around lake margins and in well vegetated, shallow downstream regions of streams. Remarks: Although not recorded from the modem fauna at Ioannina as part of this study, it is possible that further detailed sampling (particularly in the extensive reed beds) would recover this species. Genus Heterocypris CLAUS, 1892 Heterocypris rotundatus (BRONSHTEIN, 1928) Plate VI, fig. D-E 1928 Cyprinotus rotundatus BRONSHTEIN, Rab. Sev.-Kavk. Gidrobiol. St., 2 (2-3), p.90, 112, p1.8 , figs. 16-21. Material examined: Fossil material from the Holocene interval of 284. Occurrence: The genus Heterocypris has a very broad distribution and is known from almost every continent. Many species are recorded from the Balkans and circum­ Mediterranean zone (e.g. Laffler and Danielopol, 1978). H. rotundatus is known from Eernian deposits in Germany (Fuhrmann and Pietrzeniuk, 1990) and from Plio­ Pleistocene deposits on the Greek island of Kos (Mostafawi, 1988). FAUNA AND BIOSTRATlGRAPHY. 141 Ecology: The specific ecological preferences of H. rotundatus are not well-known, but Heterocypris sp. are generally considered to be hardy and capable of tolerating a broad range of salinities. Remarks: In their study of the Upper Pliocene fauna from the Katsikas site, Guemet et al. (1977) note the occurrence of Cyprinotus sp. (currently known as Heterocypris sp.). It is possible that the form collected by Guemet et al. (1977) is H. rotundatus, but this is impossible to ascertain without critical comparison of material. Genus Prionocypris BRADY AND NORMAN, 1896 Prionocypris sp. Plate VI, figs . F-G Material examined: Fossil material from the LGIT interval of 284. Occurrence: This is generally a poorly-known genus, represented by two species, P. zenkeri (CHYZER AND TOTH, 1858) and P. serrata (NORMAN, 1862). The latter is the nominate species, since the true status of P. zenkeri remains uncertain (e.g. Danielopol and McKenzie, 1977; Griffiths, 1995a). While both occur across Europe in a range of Pleistocene and Holocene deposits (many of which require further confirmation given the uncertainty over the species), only P. zenkeri has been recorded from Greece (Hiltermann and LUttig, 1969). Ecology: Given the confusion over the taxonomy, ecological data are difficult to ascertain. In core 284, Prionocypris occufd with L. cf. ostrovskensis, 1. slavonica, D. stevensoni and C. permanenta, suggesting that it is likely to be a littoral, cold water species that has a preference for muddy substrates and aquatic vegetation. Other remarks: Although Prionocypris sp. only occurs at a single level in the core (23 .30m), it constitutes 20% of the ostracod fauna at this level. This is somewhat puzzling and is unlikely to be explained satisfactorily without further ecological information being available. FAUNA AND BIOSTRATIGRAPHY • 142 6.3.3 Modern Ostracod Fauna During September, 1994, eight sediment samples were collected from the littoral zone of Lake Pamvotis (section 3.2.6). The sample site locations are shown in fig 6.3 and briefly described in appendix A. Although no live specimens were collected, many carapaces still contained the remnants of soft parts, indicating that the animals still live in the lake today. Due to the qualitative nature of the sampling technique employed, it is possible that the following list of modern species is incomplete. A total of nine species were recovered: Darwinula stevensoni Cyprideis torosa /lyocypris bradyi /lyocypris slavonica Candona cf. dedelica Candona permanenta Cypria ophtalmica Cypridopsis vidua Eucypris virens As previously described (section 4.2.2), modern Lake Pamvotis is a relatively shallow « lOm), freshwater, eutrophic water body with a range of clay, silt and sandy substrates. These factors are reflected by the modern ostracod fauna, most of which have ecological preferences for muddy or silty substrates and for the presence of abundant aquatic vegetation. In addition, all of the species present are able to tolerate fresh - oligosaline conditions. The range of microhabitats within the lake is also reflected in part by the ostracod fauna found at those sites. For example, sites 4 and 7 are low-energy, shallow littoral areas with dense macrophytic vegetation (see fig. 6.3 and appendix A). The fauna recovered from these sites include Cypria ophtalmica and Cypridopsis vidua, both of which favour littoral areas with muddy substrates and macrophytic vegetation. Sites 2, 6 and 11 are located along the north-eastern shore, where there are abundant reed beds. Cypria ophtalmica is also often associated with reed beds and is a major constituent of the fauna at these sites. Site 1 (a shallow-dipping beach north of Ioannina city) is interesting, as prevailing winds ensure that it experiences relatively high-energy conditions compared with other sampling locations. The fauna at site 1 is dominated by Cyprideis torosa, a hardy, eurytopic and euryhaline species which represents 82% of the ostracod fauna at this location. The valves are robust and well calcified, enabling it to tolerate a higher energy environment than other, more delicate genera. It occurs with /lyocypris slavonica (thought to be able to tolerate moving water) and Candona pennanenta, a eurytopic FAUNA AND BIOSTRATIGRAPHY • 143 species that generally dominates both the modern and fossil fauna. It is interesting that Cyprideis torosa is found only at this site. One likely explanation is that although it is a eurytopic species, all the other sampling sites experience considerably lower energy conditions, which may be unsuitable for it. Other species might therefore have a competitive advantage in these low-energy, vegetation-rich environments with muddy rather than silty or sandy substrates. 6.3.4 Taphonomy Before discussing the fossil ostracod faunas, some aspects of their taphonomy must first be considered. The fossil Candona assemblages all showed a distinct bias in the preservation of growth stages. In particular, there were relatively few adult valves and carapaces recovered relative to other instal's. A histogram plotting the absolute number of picked instars of C. permanenta recovered from the last glacial - Holocene section of the core is shown in fig. 6.4 (n = 60). It shows a definite skew towards the A-4 / A-5 instal's, with the number of adult / A-I valves recovered being the smallest group. This graph bears a remarkable resemblance to the 'type-C' distribution pattern described by Whatley (1983), which he interprets as being characteristic of a low-energy death assemblage. He suggests that the low number of larger valves is due to some degree of weak current action 'winnowing' out the heavier valves. If weak current activity was the cause of this preservational bias in the candonids (the largest ostracods present), then a more balanced distribution of instal's of the smallest species might be expected, since the current velocity would presumably be sufficient to carry all or most of their growth stages. In fact, most of the smaller species (e.g . Cypria ophtaimica, Leptocythere cf. ostrovskensis) also show a preservational bias, although this time it is almost entirely skewed towards the adult valves; the smallest instars are hardly represented. This is most probably an artifact caused by the smallest size of sieve used in preparing the sediments (l50llm), which may have lost the smaller instal's of these particular species. Clearly, a reappraisal of the instar distribution of the smallest species would require resieving the sediment samples using finer-mesh sieves. It is not possible to compare these results with modern instar distributions, as the original sampling method was not rigorously quantitative. In addition, many of the higher-energy sample sites (e.g. the beach at site 1) would already possess a skewed distribution pattern. Further sampling, preferably of lake-bottom sediments across the entire lake, would be useful in determining not only instar distribution, but also benthic community distributions. FAUNA AND BIOSTRATIGRAPHY. 144 2000~--------------------------------~ 1500 "0 <.) ..>:: u .s.. V> <.) ;> C;; ;> 1000 "--0 0 I':: <.) S '0 V> .0 --< 500 0 C<) If) ... -< -< -< <.) :;a -- 8 ~ N " "0 "0 --< I':: '" \0 -< Fig. 6.4 Instar distribution of Candona permanenta picked from the last glacial - Holocene interval of core 284. The evidence for current activity therefore suggests that the ostracod fauna in core 284 is representative of a death assemblage. This means that the association of species found in the fossil record might not necessarily reflect the association of these species when they were alive. This obviously has serious implications for the interpretation of the faunal counts in the core. In general, the recovery of specimens has been poor; counts have consistently been below the 350 valves required from each level to make a statistically robust assessment of faunal composition. In addition, the ecological information available for each species is not particularly precise or detailed, limiting palaeoenvironmental inferences to very general statements. It is therefore unlikely that the added complication of what is likely to have been a relatively small degree of transport will have a significant effect on the final interpretations. Only if the faunal counts had been consistently high would potentially detailed interpretations be affected by this problem. Although all of the above points must be borne in mind when analysing the fossil data, a useful first order FAUNA AND BIOSTRATIGRAPHY. 145 assessment of faunal structure and succession through the selected parts of the core can still be achieved. 6.3.5 Fossil Ostracod Fauna: Last Glacial - Holocene The section of core 284 that includes the last glacial - Holocene (2S-1.4m) was sampled for ostracods at 20cm intervals, as described in section 3.2.7. A total of 12 species were recovered: Darwinula stevensoni Leptocythere cl ostrovskensis Paralimnocythere cf. compressa /lyocypris bradyi /lyocypris slavonica Candona cf. dedelica Candona permanenta Cypria ophtalmica Cypridopsis vidua Eucypris virens Heterocypris rotundatus Prionocypris sp. The results of the faunal counts are plotted in fig. 6.S, presented as valves per gramme of dry sediment against depth. The plotting package used, psimpoll 2.2S (written in C by K.D. Bennett, Department of Plant Sciences, University of Cambridge), was originally developed for presenting pollen data. However, many of the features (such as its ability to statistically calculate a zonation scheme) can equally be applied to faunal data. Five distinct faunal zones are recognised. After an initial description of each zone, the data are discussed. 10-1 2S.00-24.0Sm V ruiable values of Candona permanenta, occasional Darrvinula stevensoni and Leptocythere cf. ostrovskensis. End of zone marked by abrupt disappearance of Candona cf. parvula. 10-2 24.0S-16.70m Highly vru'iable and oscillating values of C. permanenta. Appearance of /lyocypris slavonica. Single appearance (at 23.30m) of Prionocypris sp.. Variable values of L. cf. ostrovskensis and D. stevensoni, although the former . is more common at the beginning of the zone, the latter more common towards the end. Rare OCCUlTence of Cypria ophtalmica, particularly at the end of the zone. Between approximately 23.0- Ioannina 284 Last Glacial - Holocene O'tracod Fauna Depth m 4 10 11 12 13 14 15 16 17 IS 19 20 21 22 23 24 25 ~,~ tot /' s'~ ;.;.'~ o,S j,.' ~ )..i' , ~ ~ ~ F . ,,~,o ~,r, f) 0"'<1. ~..,o ·ss ;;5 ~ ::j c;J ~ ~ '"tl ::r: "<: • -.j:>. 0\ FAUNA AND BIOSTRATlGRAPHY. 147 22.0m, all taxa experience a decline followed by a recovery, highlighted particularly in Candona permanenta and 1. slavonica. 10-3 16.70-1S.2Sm Sharp decline of Candona permanenta to very low values at the beginning of the zone, recovering slightly by the end of the zone. The only other species represented is a single level with D. stevensoni. 10-4 lS .2S-S.S0m Lengthy zone featuring oscillations in the values of C. pelmanenta, with a distinct peak at approximately lOm and a noticeable trough between approximately 7.S-6m. Other species present (sproadically) are L cf. ostrovskensis, D. stevensoni and Cypria ophtalmica. 10-5 S.SO-1.30m Final zone, commencing with a very sharp peak in Candona permanenta, which then declines to a low level again. Cypria ophtalmica increases in value through the zone. Candona cf. dedelica and D. stevensoni are present sporadically. Several species appear at the end of the zone: Cypridopsis vidua, Heterocypris rotundatus, Jlyocypris bradyi, Eucypris virens and Paralimnocythere cf. compressa. With the limited, ecological information available for these species, even first order interpretation of the faunal succession is difficult. That there is a definite succession is not in doubt; different species disappear and appear over the interval and there is a definite suggestion of higher order variability in the data. The dominance of the fauna throughout by C. permanenta would indicate that the site was probably situated in a sublittoral, possibly profundal location for much of the time. The low abundances of the littoral species, coupled with the preservational bias of the growth stages (discussed in section 6.3.4, above) also suggests that the site was in relatively deeper, rather than shallower, water depths. This confirms the lithological and strati graphical information obtained by IGME (section 2.3) and their interpretation that core 284 was taken from the deepest of the sub-basins. The main points of each of the faunal zones (fig. 6.S) are now discussed in turn. The end of zone 10-1 witnesses the abrupt disappearance of Candona cf. parvula, coinciding with what has been interpreted as the end of the LGM (section 7.S.3). Since this species is present below this point into at least into MIS-6 (see section 6.3.6, below), its disappearance at the end of the LGM is a valuable biostratigraphical marker. The cause of this extinction event is not clear, since very little is known of its ecological FAUNA AND BIOSTRATIGRAPHY. 148 tolerances. As it is also present in the Eemian, it is obviously a reasonably eurythermal species. However, it is possible that conditions became too severe at the height of the last glacial and either the temperature became too low, or reduced lake levels (see discussion of Dreissena beds, section 6.2.3) ensured that its prefelTed sublittoral benthic habitat became restricted. Despite the oscillations of C. permanenta throughout zone 10-2, five other species show a reasonably clear succession. At the beginning, l. slavonica and Prionocypris sp. appear, only to be replaced by greater dominance of L. cf. ostrovskensis and D. stevensoni. With the exception of a very brief appearance in the middle, Cypria ophtalmica only appears at the very end of the zone. Although this part of the record has been interpreted as including the Lateglacial interstadial (chapter 5), lack of precise ecological information makes a detailed interpretation difficult. However, in the broadest sense, the succession could represent the recovery and deepening of the lake following the LGM, with littoral species such as I. slavonica giving way to slightly deeper water species such as L. cf. ostrovskensis and D. stevensoni. 10-3 witnesses a sharp decline in C. permanenta, with a minimumin the middle of the zone, at around 16m. A possible interpretation for this part of the record is that it reflects the Younger Dryas (section 5.8), thought in the eastern Mediterranean to be an arid, cold phase (e.g. Tzedakis, 1993; Rossignol-Strick, 1995). Productivity is likely to have been low during this time, reflected by the decline in the population of C. permanenta. It is not possible from these data to determine whether this was accompanied by a lake-level fall. 10-4 sees a recovery by C. permanenta, although it oscillates markedly throughout this zone and experiences a pronounced crash between -7.5-6m. This minima coincides with a distinct litho logical change to a shelly calcareous silt, which could well reflect a shallowing of the lake. Other species are present only sporadically throughout the zone. This part of the record has been interpreted as the first part of the Holocene (section 5.8). 10-5 begins with a marked increase in C. pennanenta, which then declines towards the end of the zone. Cypria ophtalmica also experiences a rise at the beginning of the zone and gains in importance. As a hardy eurytopic littoral species, C. ophtalmica is often successful in stressed environments. This zone coincides with another change in lithology (to a shelly, clayey silt), which could be a reflection of the continuing shallowing of the lake. The occurrence of other littoral species such as Eucypris virens and Cypridopsis vidua towards the end of the zone, supports this interpretation. FAUNA AND BIOSTRATlGRAPHY. 149 Interestingly there is no record of Cyprideis torosa, another hardy eurytopic species which currently dominates the ostracod fauna at site 1 (a high-energy shallow beach). It is possible that despite the shall owing of the lake, the site of 284 never experienced sufficiently high-energy conditions. It is also possible that it has only been able to thrive in the lake in recent historical times, perhaps due to a change in nutrient status caused by the effects of pollution. In summary, therefore, it seems that the ostracod fauna through this part of the core records the recovery of the lake following the LGM (and the return of the core site to deeper waters), followed by a gradual shallowing of the lake during the Holocene. This interpretation is discussed further in section 7.5.3, when it is compared with the palaeoenvironmental information provided by the mollusc an fauna. 6.3.6 Fossil Ostracod Fauna: Eemian The section of core 284 that includes the Eemian (l00-83 .2m) was sampled for ostracods every 20cm, as described in section 3.2.7. A total of 6 species were recovered: Darwinula stevensoni Leptocythere cf. ostrovskensis Jlyocypris slavonica Candona permanenta Candona cf. parvula Cypria ophtalmica In general, the fauna was relatively sparse and poorly preserved compared with that from the last glacial - Holocene. The results of the faunal counts are again presented as valves per gramme of dry sediment against depth (fig. 6.6). Eight distinct faunal zones are recognised. After an initial description of each zone, the data are discussed. le-l 100.0-98.30m Very sparse zone, with only occasional valves of Candona pennanenta or Leptocythere cf. ostrovskensis. le-2 98.30-96.10m Increase in value of C. permanenta at the beginning of the zone, followed by a decline in values (from -4 valves/g to -0.2 valves/g) at around 97m, followed by an increase in values again at the end of the zone. C. cf. parvula and L. cf. ostrovskensis are both recorded at the very beginning of the zone. Ioannina 284 Eemian Ostracod Fauna Depth m 84 85 86 87 88 89 90 91 92 93 94 95 96 97 98 99 lOO \~ ,<:- ~<:' <,,' ~' ,~ ~o' cl' ~ 0 ~o~ cl' .3>~ ~<' (;.,.~ I I 2 4 6 0 2 Values expressed as valves per g .3>~ ,j;$" \)~ i:-' <:-~o ,< ~\' ,.i' ,0Cl' V~ (;.,. ~,~ .~ ,,0 o~ .~~ (;-~' ~ 0"-~ ... o- C;1~ ~~~ o o o Fig. 6.6 Ostracod fauna from the Eemian interval of core 284. See text for zonation scheme details . 10-8 10-7 10-5 10-4 10-3 10-2 10-1 ~ ~ c::: s;: ~ ~ tl:i ...... a V:l ;;5 ~ :::l CJ ~ "tI ::t: ""<: • Vl o FAUNA AND BIOSTRATIGRAPHY • 151 lea 3 96.1O-90.10m Lengthy zone with a velY poor fauna. Low values of C. permanenta and a record of C. cf. parvula from a single level. le-4 90.1O-87.70m Sudden rise in C. permanenta at the beginning of the zone. Present at relatively high values throughout. Values of C. cf. parvula and L. cf. ostrovskensis increase towards the end of the zone. le-S 87.70-84.90m Oscillating values of C. permanenta. C. cf. parvula peaks at beginning and end of the zone; absent in the middle. Oscillations in values of L. cf. ostrovskensis, broadly matching those in C. permanenta. Single occurrence of Cypria ophtalmica at the beginning of the zone and of Darwinula stevensoni at the end of the zone. le-6 84.90-84.70m Zone spanning a single, particularly rich sample at 84.80m. VelY high values of Candona permanenta and C. cf. parvula. L. cf. ostrovskensis also recorded. le-7 84.70-84.10m Very low values of C. pennanenta at beginning of the zone, increasing towards the end of the zone. Low values of L. cf. ostrovskensis at the beginning and the end of the zone. C. cf. parvula and D. stevensoni both occur towards the end of the zone. le-8 84.1O-83 .20m Low values of C. permanenta, C. cf. parvula and L. cf. ostrovskensis. Because of the relative sparseness of the fauna, interpretations are even more difficult than for the last glacial- Holocene interval. In general, the lack of littoral species and the dominance of the fauna once again by Candona pennanenta would suggest that the site was located in the sub-littoral or profundal zone of the lake. The interpretations suggested below are later compared with other proxies through this interval (section 7.5.1), in particular the pollen record. The first zone, Ie-1 , contains a very sparse fauna indeed, which makes any palaeoenvironmental interpretation almost impossible. This part of the record has been interpreted as representing the velY end of the penultimate glaciation (end of MIS-6). It is possible that the glacial conditions meant that productivity in the lake was low, accounting for the lack of material. FAUNA AND BIOSTRATIGRAPHY • 152 C. permanenta rises steeply during zone le-2, although frequencies fall at -96.80m but recover again soon after. This part of the record is thought to represent the beginning of the Eemian (section 7.5.1). The carbonate and ostracod (5 180 records both oscillate sharply at the beginning of the Eemian, described as an abrupt 'Younger Dryas-type' cooling event before the full interglacial commences. The minima in C. permanenta coincides with this abrupt oscillation, probably representing a drop in productivity during this cooler period. le-3 is a lengthy zone, with only low values of the two Candona taxa represented. This part of the record has been interpreted as representing the first part of the Eemian, thought to be the warmest part of the interglacial (e.g. Tzedakis, 1991). The absence of ostracod fauna is puzzling, since warm and wet conditions should have promoted increased aquatic productivity. It is possible that the lake was relatively deep during this time (i.e. too deep for the Candona fauna), since it is known from studies in Lake Ohrid (e.g. Stankovic, 1960) that C. parvula prefers epibenthic rather than true benthic habitats. This may also be true of C. permanenta, although once again, the lack of precise ecological information for these species makes any interpretation very difficult. The beginning of le-4 sees a resurgence of C. pennanenta and the appearance of L. cf. ostrovskensis towards the end of the zone. If the assumptions concerning the ecological preferences of C. pennanenta made above ar'e correct, then this zone might represent a loweri~ig of the lake level (reduced temperatures and/or precipitation?) to return the site of 284 to a sub-littoral/profundal habitat once more. Zone le-5 sees a slight lowering in the average values of C. permanenta, but there is a marked rise in L. cf. ostrovskensis and C. parvula. The frequencies of all three taxa fall at -86m. These oscillations could again be due to fluctuations in lake level or productivity. The minima coincides with drops in the carbonate, 8180 and 813C records. This might represent a brief cool period within the main interglacial, during which productivity levels were reduced. le-6 is a narrow zone consisting of one particularly rich sample, with a very abundant Candona fauna. It is likely that this represents a brief time of optimal sublittoral conditions with plenty of decaying organic matter on which to feed. le-7 is a return to similar conditions seen in le-5, with moderate levels of candonids and a few other taxa poorly represented. FAUNA AND BIOSTRATIGRAPHY • 153 le-8 sees a return to the situation seen in le-I, with low Candona counts and the occasional L. cf. ostrovskensis. This part of the record has been interpreted as the end of the Eemian and the beginning of the stadial MIS-5d. The sudden resumption of much cooler and drier conditions can also be clearly seen in the carbonate and isotopic records (section 7.5.1). In summary, therefore, it seems that the ostracod fauna through this pmt of the core records the behaviour of the lake through the Eemian. Starting with a sharp and oscillatory inferred rise in lake level, relatively deep water levels were maintained until the beginning of zone le-4, when the beginning of a slight drop is inferred. For the rest of the Eemian, levels appear to have fluctuated until the end of zone le-7, when there was a return to the lower lake levels seen at the very beginning of the interval. This interpretation is discussed further in section 7.5.1, when it is compm·ed with the palaeoenvironmental information provided by other proxies. 6.3.7 Other Intervals of 284 This study has only considered in detail the modern, last glacial - Holocene and Eemian ostracod faunas, representing only -16% of the total core length. Time did not permit a comprehensive examination of other parts of the record, but several pilot levels were analysed from each of the intervals interpreted as glacials and interglacials (chapter 5) . Although unsatisfactory from a both a biostratigraphical and a faunal stmcture point of view, it is still of use in estimating the overall range of some of the species involved. For example, Candona permanenta occurs throughout the entire core, whereas C. cf. parvula only appears in the record between 170-140m (i.e. during MIS-7). Other species, such as /lyocypris slavonica and Leptocythere cf. ostrovskensis, occur sporadically and in very low abundances throughout the core. However, the main observation is that the ostracod fauna is dominated throughout by the candonids and in some cases, such as the sample analysed from 260.74m, the abundances are very high. This would suggest that the core site was chiefly located in a sublittoral or even profundal setting for much of the time, confirming previous assumptions based on lithology and stratigraphy (section 2.3). Clearly, the potential for fmther high resolution faunal analyses of this material is considerable. FAUNA AND BIOSTRATIGRAPHY. 154 6.4 SUMMARY This chapter has discussed the analysis of the modern, last glacial - Holocene and Eemian mollusc an and ostracod faunas from Ioannina. The taxonomy, occurrence and ecology of twenty-one aquatic mollusc and fourteen ostracod taxa were reviewed and their relevance to the Ioannina sequence discussed. Some of the problems associated with endemic taxa were also outlined. This represents the first study of Quaternary mollusc an faunas and the only comprehensive study of the ostracod faunas (both modern and fossil) from Lake Pamvotis. It also represents the first time that poorly­ known endemic faunas from the lake have been properly described and illustrated. Examination of both the molluscs and ostracods in 284 provided only low faunal counts, meaning that the usual statistically derived analysis methods could not be used. However, it was still possible to derive useful palaeoenvironmental information. For example, the presence of Dreissena beds in the core material helped to pinpoint periods of low lake level (palticularly at the LGM). The succession of various ostracod taxa were also used to determine lake level variation. In assessing the biostratigraphical importance of the faunas in the core, it was shown that the low frequencies of the molluscs in particular precludes their use for these purposes. Although a similar situation existed for the ostracods, the appal'ently ablUpt disappearance of Candona cf. parvula at a level in the core interpreted as being the LGM may constitute a useful biostratigraphical marker. Clearly, there is a need for this to be replicated in other cores before it can be generally applied. The faunas from the core al'e more useful in helping to interpret palaeoenvironmental conditions than as biostratigraphical tools. 7. INTERPRETATION AND SYNTHESIS OF RESULrrS 7.1 INTRODUCTION In prevIOus chapters, results have been presented individually, without detailed discussion. In this chapter, the interpretation of those results is considered in full and their stratigraphical importance assessed using the age model developed in chapter 5 . Where appropriate, comparisons are made with other data obtained as part of this study. A synthesis of all the results is then presented in order to derive a comprehensive palaeoenvironmental history of the lake basin over the last 600ka, with special attention given to those intervals of the record that were singled out for detailed analysis. The broader significance of the Ioannina 284 sequence is discussed in chapter 8. 7.2 SEDIMENT ANALYSES The physical and chemical composItion of the core material has been extensively analysed. The se quence is thought to be continous because of the lack of sharp lithological breaks or sedimentological indicators of hiatus or lake emergence (e.g . evaporites, soil or peat horizons, oxidised layers) . The dominantly clayey silt lithology with relatively low «30%) carbonate levels is typical of profundal sediments from eutrophic mid-latitude temperate hard-water lakes (Dean, 1981). In section 3.3.1 the four main constituents of sediments from lakes such as Pamvotis were listed, namely detrital clastic material, biogenic silica, carbonate minerals and organic matter. SEM analysis demonstrated the low allogenic input to the borehole site from detrital material, although the possibility of limited aeolian input of matelial derived from the deserts of North Africa was considered (section 2.3). SEM analysis also confilmed the high level of biogenic silica present in the sediment (largely consisting of diatomaceous material and a siliceous cement binding individual grains together). Jones and Bowser (1978) consider organically-derived silica (i.e. due to diatoms) to be the most significant authigenic (endogenic sensu stricto) contributor of silica in lake systems. Regarding the final two sediment constituents, it has often been suggested that organic matter and/or carbonate levels can be used as proxies for lake INTERPRETATIONS AND SYNTHESIS. 156 productivity. To assess the validity of this statement (and to interpret the curves illustrated in figs. 4.4 and 4.5), the origins of each are now discussed in some detail. 7.2.1 Carbonate Content Carbonate minerals within lake sediments can be derived from a variety of sources. Kelts and Hsii (1978) recognise four main processes: they can be allogenic in origin, having been eroded from the catchment; they can be bioc1astic, consisting of debris from calcareous plants and animals; they can be produced by primary inorganic precipitation (induced by either physical or biogenic factors); or they can be derived from early diagenetic reactions. Dean (1981) notes that most carbonate in temperate hard-water lake sediments is either inorganically precipitated or biogenically-induced. Greater seasonal temperature variations in the littoral zone of a lake ensure that the rate of inorganic carbonate precipitation is higher than in profundal regions. Detailed discussion of the chemistry governing the precipitation of carbonates in lakes is beyond the scope of this study, but Wetzel (1975), Kelts and Hsii (1978) and Dean (1981) all give comprehensive reviews. Essentially, assimilation of CO2 from the water by the photosynthetic withdrawal of CO2 by abundant algae and aquatic macrophytes increases the pH, resulting in higher rates of biogenic ally-induced carbonate formation (demonstrated, for example, by calcareous enclUstation of plants). The proportion of detrital (allogenic) material and of bioc1astic carbonate (debris from ostracods, molluscs, charophytes and the like) is also significant. Littoral zone sediments are therefore generally characterised by a higher total percentage of carbonate than those derived from the profundal zone. By comparison, carbonate production in the profundal zone is generally dominated by inorganic and, in particular, biogenically-induced precipitation (largely due to the photosynthetic activity of phytoplankton). Bioc1astic carbonate is much less important and detrital contributions are also usually minor, since most allogenic material remains trapped in the littoral zone (Dean, 1981). However, detrital material can sometimes be deposited in the profundal zone, particularly if it is fine-grained and is canied as suspended load by inflowing rivers (Kelts and Hsii, 1978). When this is the case, allogenic carbonates can be almost indistinguishable from primary carbonate material. Another possibility is for littoral material to be transported to deeper levels by turbidity CUlTents triggered either by the excess load carried by flooding rivers (Kelts and Hsii, 1978), or by earthquakes. Here again, distinguishing between allogenic and primary carbonates can be almost impossible. Neither of these possibilities are a major problem INTERPRETATIONS AND SYNTHESIS • 157 at Ioannina. The core site was apparently profundal for most of its history (section 2.3) and the lake has no fluvial input, limiting the possibility of suspended material reaching the centre. Although Epirus is a tectonic ally active region, turbidity currents triggered by flood events can also be largely ruled out, as they usually operate only where the lake is moderately or steep-sided (e.g. Ludlam, 1974). This is not the case at Ioannina, where gradients are gentle. Turbidity current deposits can also be recognised by distinctive bedforms (e.g. graded bedding), differences in colour to the normal sediment and the presence of large quantities of (usually fragmented) littoral bioc1astic and organic material. These features are absent in core 284. Detrital carbonate material is therefore expected to be an extremely minor component of the core sediments, an assumption borne out by SEM analysis. As mentioned above, the carbonate content of sediments is often correlated with primary lake productivity. Increased aquatic productivity (caused, for example, by an increase in temperature) will result in enhanced rates of photosynthesis by aquatic macrophytes, so increasing the amount of biogenic ally precipitated carbonate. In addition, raised temperatures may also encourage inorganic precipitation of carbonate from the water column. In simple lake systems, a strong linkage between productivity and carbonate content can often be demonstrated. However, this is not always the case. Care must be taken to avoid indiscriminately interpreting carbonate content from lake records as a proxy for aquatic productivity without first acquiring a detailed understanding of how each individual lake system operates. Decay of organic material within the sediment lowers the pH and generates CO2, which can lead to carbonate dissolution. Diagenetic effects such as this can be severe; in these cases, the amount of carbonate preserved within the sediment bears little relation to that produced by primary lake productivity (e.g. Dean, 1981). At Ioannina, however, SEM analysis of authigenic carbonates (particularly ostracod carapaces) shows no evidence for carbonate dissolution. High (>2) Mg/Ca ratios of the pore waters can also promote diagenetic alteration of primary carbonates (Muller et aI., 1972). As outlined in section 4.2.2, the Mg/Ca ratio of the lake waters at Ioannina is low (0.37), confirmed by the precipitation of platey hexagonal calcite crystals, seen under the SEM. This suggests that pore-water fluids would have a similarly low Mg/Ca ratio. It is therefore assumed that any diagenetic alteration of carbonates within the sediment are negligible. The other possible contributor of calcite to the sediments of core 284 is from bioc1astic sources. For most of the history of the sequence, the absence of molluscan remains (dominantly littoral or sub-littoral in habitat preferences) would support the stratigraphical evidence that the core was located in a deep sub-basin. The dominance INTERPRETATIONS AND SYNTHESIS • 158 of the fauna below this level by profundal benthic ostracods (Candona permanenta) also supports this assumption. Molluscan fragments first occur in any frequency in the sediment above about 145m, suggesting that the lake-level began to drop. A reduction in lake-level (for whatever reason) would have resulted in the setting of 284 becoming progressively more littoral. This is discussed at length in section 7.3.1, below. Despite careful avoidance of obvious shell fragments when sampling, increased bioclastic input would still affect the level of measured carbonate content in the core. This can clearly be seen at depths such as 26m and 32m (fig. 5.3), where the lake shallowed sufficiently for shell-beds of Dreissena to develop. Relatively high carbonate content values were recorded at these levels, even though obvious shelly material was removed from the sediment sample prior to measurement. It is therefore proposed that below 145m the carbonate curve can be used as a proxy for aquatic productivity with reasonable confidence. Above this depth, however, any interpretation of the carbonate curve should be regarded with caution, as values are likely to be biased by bioclastic input. 7.2.2 Organic Matter Content Dean (1981) outlines two main sources of organic matter in temperate hard-water lake sediments. It may be allogenic, derived chiefly from catchment vegetation, or it may be autochthonous, derived either from vegetation in the littoral zone, or from pelagic phytoplankton and zooplankton. After detailed consideration of a series of lakes from the English Lake District, GOl'ham et al. (1974) concluded that most organic material in eutrophic lakes is authochthonous in origin and that allogenic material only becomes significant in the most oligotrophic water bodies. However, it is well established that primaly production of organic matter "is not necessarily related to the relative amount of organic matter that ultimately becomes part of the sediment" (Dean, 1981: p.225). Most organic material (allochthonous or autochthonous) that accumulates in the littoral zone is subject to destruction by benthic respiration and aerobic decay, particularly in eutrophic lakes where productivity is always relatively high. Even in the water column, phytoplankton and zooplankton debris is subject to aerobic decay within the epilimnion and to anaerobic decay within the hypolimnion and sediment. It is worth noting that even though dissolved inorganic carbon (DIC) is the major reservoir of carbon in a lake system, by a factor of at least 10 over pruticulate matter (Wetzel, 1975), it contributes very little to the proportion of organic carbon eventually stored in the sediment. As a result, only about 7% of the organic carbon produced in the lake actually becomes preserved in the sediment (Wetzel, 1975). INTERPRETATIONS AND SYNTHESIS • 159 Because of the significant amount of organic carbon destroyed in both the water column and sediment, there is often only a very weak conelation between primary lake productivity and the amount of organic matter finally preserved in the sediment (Dean, 1981). Care is therefore required in the interpretation of organic matter content of lake sediments. This also explains the often weak correlation between carbonate content (in lakes where this is strongly related to productivity) and organic matter content. At Ioannina, even though carbonate is thought to be a reasonable indicator of productivity below 145m (outlined above), the covariance between the two curves is reflected by a low r-value of 0.26. A comprehensive interpretation of the total organic matter curve in this case is therefore difficult and the points outlined above must be borne in mind. Accordingly, when discussed as part of the overall synthesis of the core data (section 7.5), it is refened to in only the broadest terms. 7.2.3 Magnetic Susceptibility Although magnetic susceptibility measurements were taken at a relatively coarse sampling interval along the entire core (approximately every 1m), the results were nevertheless sufficient to pennit conelation with core 249 (section 5.1). In addition, the results can be used to derive meaningful palaeoenvironmental information. A reasonable first-order anti-correlation with the carbonate and organic matter curves (fig. 7 .1) suggests that there was higher erosion and inwash from the catchment during glacial phases. This was possibly due to a poorer degree of soil surface stability originating from reduced vegetational cover. Nevertheless, higher order variability in the magnetic susceptibility curve indicates that other factors, for example changing erosional and weathering regimes, also affected the concentration and rate of magnetic mineral inwash into the lake. In section 4.1.2 it was suggested that the magnetic carrier in the intervals displaying very high susceptibility values had characteristics similar to magnetite/maghaemite. It is important to consider the origin of this canier. As mentioned in section 3 .2.2, pedogenic enhancement of soils can occur even on bedrock that lacks primary magnetic minerals, such as limestones (e.g. Longworth et al., 1979; Dearing, 1979; Flower et al., 1984). Studies of the magnetic enhancement of topsoils have demonstrated that the fine-grained (sub-micron) ferrimagnetic iron oxide minerals formed in this way are often either thought to be magnetite (Fe30 4) or maghaemite (yFe20 3) (e.g. Le Borgne, 1955; Longworth et al., 1979). The pe do genic evolution of these minerals is poorly understood, although Mullins (1977), Longworth et al. (1979) and Dearing et al. 0.0 10.0 20.0 30.0 40.0 50.0 60.0 70.0 80.0 90.0 100.0 110.0 120.0 § 130.0 140.0 ..c 0.. 150.0 0) Cl 160.0 170.0 180.0 190.0 200.0 210.0 220.0 230.0 240.0 250.0 260.0 270.0 280.0 290.0 300.0 310.0 ::e f f f 0 5 10 15 Organic Matter Content (%) f 20 0 10 20 30 40 Carbonate Content (%) 50 -1 0 2 3 Magnetic Susceptibility (xlo-7m3kg- 1) 4 5 Fig. 7.1 Comparison of organic matter and carbonate contents with magnetic susceptibility. Zones of anti-correlation are shown (discussed in text). ~ ~ t;j :::>;, '"tl :::>;, tll ~ :::l <::) ~ ~ ~ V) ~ 5l ~ • ...... 0\ o INTERPRETATIONS AND SYNTHESIS. 161 (1985) all suggest several possible mechanisms, including burning and gradual redox processes occurring under nOlmal soil forming conditions. In her study of sediment cores from the Kopais Basin in central Greece, AlIen (1986) carried out detailed magnetic analyses and determined the carrier to be dominantly magnetiteimaghaemite in the sediments younger than about 12.5ka BP and dominantly haematite in the sediments older than this. She also acknowledged the probable contribution from airborne dust (coated in what was probably haematite) derived from the Sahara. The difference in magnetic mineralogy in the cores was explained by advocating some of the conclusions of Tite and Linnington's (1975) study on the effects of climate on the magnetic susceptibility of soils. She suggested that 'MeditelTanean' climatic conditions re-established at the end of the Lateglacial and during the Holocene would have favoured the reduction (under humid winter conditions) and subsequent reoxidation (under arid summer conditions) of minerals such as haematite and goethite into magnetiteimaghaemite. The soils in the Ioannina catchment are rich in the iron oxide minerals goethite and haematite (section 2.3). On the basis of the existing evidence therefore, it would seem reasonable to assume that the magnetic carrier (at least in the intervals of core displaying high susceptibility values) is magnetiteimaghaemite. There is therefore a clear potential for further detailed rock magnetic work, not only to investigate the nature of the calTier in the other levels of the core, but also to establish the exact source of these minerals. For example, work carTied out at Rhode River in Maryland, USA linked the magnetic characteristics of soils and sediment samples to enable sources within the catchment to be distinguished (Oldfield, 1983; Dearing et al. , 1985; Yu and Oldfield, 1989). Measurement of the magnetic char'acteristics of a variety of catchment lithologies in the Ioannina basin (including soils, flysch and limestone units), coupled with a detailed magnetic analysis of the core material at higher resolution may enable sediment sources to be identified and conclusions drawn as to changing erosional and drainage regimes. 7.3 FAUNAL ANALYSES 7.3.1 Lake-Levels In chapter 6, the use of faunal indicators as a relative measure of lake-level was discussed. This was also referred to when discussing the carbonate content of the sediment (section 7.2.1, above). Essentially, the faunal data obtained during this study INTERPRETATIONS AND SYNTHESIS. 162 offer a means for inferring broadscale lake-level variation. Stratigraphical information (discussed in section 2.3) suggests that for most of its history, core 284 was located in a deep sub-basin and therefore had a profundal setting. The absence of molluscan remains for most of the sequence (largely preserved in littoral or sub-littoral sediments) and the presence of benthic, profundal ostracod shells supports this interpretation. However, it would appear that during the penultimate glaciation (MIS-6), the lake-level began gradually to fall. Molluscan shells are preserved in the sediment above about 14Sm, indicating that the location of bore hole 284 was located in increasingly shallower water. This may be a result of the severe conditions at the end of the penultimate glaciation, thought to be one of the most extensive glacial phases of the Pleistocene (e.g. van Andel and Tzedakis, 1996). The pollen record from Tenaghi Philippon (Smit and Wijmstra, 1970) indicates that during this time the climatic conditions in northern Greece were likely to have been cold and arid. The presence of vegetational refugia in sheltered Balkan locations, such as Ioannina, would suggest that conditions were perhaps not equally as severe everywhere (Bennett et al., 1991; Tzedakis, 1993). Nevertheless, Lake Pamvotis is known to have been sensitive to variations in PIE (discussed in section 7.4, below). Conditions of low precipitation and relatively high evaporation during the penultimate glaciation may have forced the lake-level to fall to the point where aquatic mollusc fragments could become preserved in the sediment at the site of core 284. The subsequent mcrease in PIE during the Eemian may account for the lack of molluscan fauna through that interval. The reappearance of shell fragments at around 7Sm, during the cold stadial MIS-Sb, suggests the re-establishment of low PIE conditions. These must have persisted until the height of the last glacial, since an increasing proportion of shelly material culminated in very shallow lake-levels, recorded in the core by the presence of beds of Dreissena, a shallow-littoral freshwater mussel. A schematic lake-level curve derived from faunal evidence has previously been illustrated (fig. 6.2). Although details of Eemian and LateglaciallHolocene lake-level variations are discussed further in section 7.S, one specific example of the use of faunal data for this purpose is now given. 7.3.2 The Kastritsa Problem Near the village of Kastritsa in the south of the Ioannina basin, extensive archaeological work has been canied out on an Upper Palaeolithic rock-shelter at the base of the Kastrelaki limestone ridge (Higgs and Vita-Finzi, 1966; Higgs et al., 1967; Vita-Finzi, INTERPRETATIONS AND SYNTHESIS • 163 1978; Bailey et al ., 1983a,b). Some of the sediments found within the cave were interpreted as beach deposits (approximately 6m above current lake-level) on the basis of the graded pebble bed lithology (Higgs, et al., 1967). Hearths "within the beach deposits" were recorded and two radiocarbon determinations on charcoal yielded dates of 20,800±810 yrs BP (1-2466) and 20,200±480 yrs BP (1-2468). This has been used extensively as evidence for high lake-levels in the basin at the time of the LGM (e.g. Higgs and Vita-Finzi, 1966; Higgs et al., 1967; Vita-Finzi, 1978; Bailey et al., 1983a,b; Roberts, 1982, 1983; Prentice et al., 1992; Harrison and Digerfeldt, 1993). However, this conflicts with the pollen record from 10annina and elsewhere in the northern Mediterranean, which on the basis of Artemisia and chenopod dominated pollen assemblages, indicate an arid and cold climate at this time (e.g. Bonatti, 1966; Smit and Wijmstra, 1970; Pons and Reille, 1988; Tzedakis, 1994). It has always been assumed that the original deposits were interpreted correctly as beach sediments. Certainly, the graded water-worn pebble beds are reasonably good evidence; as Bailey et al. (l983a) point out, the distribution, size and shape of the pebbles are consistent with deposits forming on beaches of the modern day lake. Further examination of some of the original sediments (courtesy of G.N. Bailey) revealed a monospecific faunal content. Dreissena is a shallow-water bivalve that often occurs in large numbers (it appears in shell-beds in the lake today). Examination of the fine sieved fraction of these sediments (for example, to look for ostracod evidence) has unfortunately not been possible. The veracity of the dates must also be considered. The published sections (Higgs et al., 1967, fig. 10, p.23; Bailey et al., 1983a, figs. 7 and 8, pp. 27 and 28) show the hearths actually underlying the 'beach' sediments and overlying a red, stony deposit that contains charcoal and a lithic industry. Without further three-dimensional details of the excavation, the question arises as to the stratigraphical integrity of placing the hearths with the overlying, rather than the underlying sediments. Several authors have tried to resolve the situation by invoking climatic arguments. Bailey et al. (1983a, b) proposed a scenario in which lower evaporation rates accompanied reduced temperatures. Prentice et al. (1992) used water-balance and biome climatic models to reconstruct the palaeoenvironment at Ioannina during the LGM. They concluded that if the jetstream was shifted southwards during winter (as several atmospheric models have predicted), then enhanced precipitation during severe winters would result, which, coupled with summer drought, would explain the presence of semi-arid steppic vegetation at times of high lake-level. Harrison and Digelfeldt (1993) also presented the Ioannina data as their primruy evidence for high lake-levels during the LGM in the Mediterranean. Out of eleven sites quoted, only INTERPRETATIONS AND SYNTHESIS. 164 Ioannina, Xinias (Greece) and Padul (Spain) had records which stretched back to the LGM. Examination of Global Circulation Models (GCMs) for the region led them to suggest that cooler and cloudier summers, coupled with extremely dry and cold winters, would be sufficient to account for the apparent paradox. As Tzedakis (1994) points out, what many of these authors have seemingly failed to take into account is the tectonic setting of the site. As mentioned in section 2.2, Epirus has been a region of tectonic compression since the beginning of the Pleistocene (Clews, 1989). Tzedakis (1994) refers to unpublished IGME stratigraphical data gleaned from borehole studies, which shows the depth of the top lignite band shallowing markedly from the lake shore towards Kastritsa (from 229-40m). This suggests uplift of the south-eastern part of the basin, an observation that is ill accordance with the terraces seen outcropping to the east (IGSR-IPF, 1966). In addition, King and Bailey (1985) record the presence of up arched fluvial deposits at the southern end of the Kastrelaki ridge. They attribute this deformation to uplift of part or all of the ridge (although they do not try to estimate the degree or rate of any movement). Significant new mollusc an evidence has been presented as part of this study for low lake-levels during the LGM (section 6.2.3). Beds of Dreissena occur in core 284 at this time, which (as explained previously) can be used as an indicator for shallow, littoral environments. Borehole 284 is thought to have been drilled through one of the deepest sub-basins of the lake (section 2.3). It is not possible for shallow lake-levels at this central site to have been coeval with high lake-levels at the margins. It is entirely likely therefore, that the elevated beach deposits in the Kastritsa cave have been subject to uplift and so cannot be used as a reliable former lake-level indicator without a correction for tectonic movements first being applied. This may have important consequences for the Mediterranean palaeolake-Ievel studies referred to above. 7.4 CHEMICAL ANALYSES 7.4.1 Modern Waters The results of the modern water sampling (section 4.2.2) indicate that Pamvotis is a typical freshwater, eutrophic lake, with a chemistiy dominated by calcium (Ca2+) and bicarbonate (HC03} The individual sampling sites were located around the periphery INTERPRETATIONS AND SYNTHESIS. 165 of the lake (fig.3.1). In the following discussion, figs. 4.8 and 4.9 should also be consulted. Samples 11, 3 and 7 display slightly lower 813C values, indicative of plant or soil­ derived dissolved inorganic carbon (DIC). These samples were taken from sites that were located in backwater areas with abundant plant macrophytes and decaying plant matter, where lower 813C values would be expected. Site 6 was located adjacent to a freshwater outflow leading from a spring to the north-west of the lake. Its lower 8D, 813C and 8180 values and consequent position near to the meteoric water line (MWL) are indicative of non-evaporated, relatively fresh water. The substantially higher chloride and sulphate content of site 6 waters can be explained as being derived from pollution originating from the agricultural small-holdings currently lining the water­ course leading from spring to lake. The average 8 I3C value of the waters was around -3.5%0, somewhat lower than might be predicted for present-day waters in equilibrium with atmospheric CO2, The HC03- CO2 (gas) isotopic fractionation is around +8.7%0 (at 18°C) and atmospheric CO2 has a 813C value close to -8%0. This means that waters in equilibrium with present-day atmospheric CO2 would be expected to have a 8 I3C value of approximately +0.7%0, not -3.5%0. The depletion seen in the Ioannina samples is possibly because the lake waters still possess a remnant of the groundwater-derived bicarbonate, or, more likely in view of the eutrophic nature of the lake, it is because they still contain some 12C-rich carbon derived from organic matter decay (T.H.E. Heaton, pers. comm.). In other words, these figures suggest that the modern lake waters are not in full equilibrium with atmospheric CO2, The implications of the strong covariance between the 8180 and 813C values are discussed in section 7.4.4, below. 7.4.2 Sediment Isotope Geochemistry Stable oxygen and carbon isotopic measurements were carried out on bulk sediment carbonate at 20cm intervals between 100-83m, interpreted as including the entire Eemian period (section 5.8). In order that a balanced interpretation of the results (fig.4.2.1) might be attempted, the possible range of controls on stable isotopes in a lake system is now considered. INTERPRETATIONS AND SYNTHESIS • 166 (a) Oxygen The 180/160 value of calcite is a function of: (i) the temperature of calcite precipitation, i.e. water temperature; and (ii) the 180/160 of the lake water, which may be controlled by the isotopic signature of the precipitation (which may in turn be controlled by such factors as air temperature and moisture source), the PIE ratio, the isotopic signature of any dissolved carbonates from the catchment and any groundwater inputs. The origin of the bulk calcite in the profundal sediments that make up 284 is chiefly a result of biogenic precipitation in surface waters (discussed in section 7.2.1, above). If the 8180 signal recorded in the carbonates over this interval was dominantly controlled by water temperature, then the curve would be expected to become markedly more positive during the warm interglacial period. This is because of the temperature dependency of the fractionation process (e.g. Faure, 1986). In fact, a marked negative oscillation is seen across the Eemian (fig. 4.7), which is more consistent with a PIE control on 8180. An increase in the PIE ratio introduces more 160 into the system (in the form of H 2160), ensuring that 8180 decreases. Obviously, the reverse is tme during times of low PIE ratio. Pollen data derived from core 249 indicate that the Eemian was relatively warm and wet in comparison to the previous glacial period (Tzedakis, 1991), an interpretation confirmed by unpublished pollen data from core 284 (see section 7.5, below). In addition, the numerical values recorded by the 8180 curve are within the limits of what might be expected for carbonate precipitating in equilibrium at Ioannina. Using present­ day climatic data (section 2.4), a typical range of 8180 values for precipitating carbonates is calculated to be between about -4.0 to -8.0%0. Assuming that the range of temperatures and isotopic values of precipitation during the last interglacial was reasonably similar to that of today, the mean 8180 value of the bulk carbonates of around -5%0 falls comfortably within the predicted range. Since the other factors which contribute to the 180/160 of the lake water (i.e. isotopic composition of precipitation and ground water) are likely to be relatively constant factors in comparison, it seems reasonable that PIE is the dominant control on 8180 values through this interval. (b) Carbon Interpreting the carbon isotope signal through this interval is not as straightforward as for the oxygen isotope record, as there are many more potential influences on the 8l3e values. These include: (i) the surface water productivity (i.e. uptake of 12e by INTERPRETATIONS AND SYNTHESIS. 167 photosynthesis); (ii) respiration/decay of organic matter (i.e. release of 12C at depth); (iii) the isotopic composition of inflowing waters and precipitation; and (iv) the degree of CO2 exchange with the atmosphere (McKenzie, 1985). These will now be considered in turn. (i) Suiface Water Productivity. Photosynthesising phytoplankton in the surface waters of the lake preferentially incorporate 12C from the dissolved inorganic carbon (DIC) pool, leaving the DIC enriched in 13C (McKenzie, 1985). As noted in section 7.2.1, this removal of 12C from the DIC produces a disequilibrium in the bicarbonate­ carbonate system, raising the pH and allowing calcite to precipitate with an enhanced ()13C composition. Carbonates precipitated in surface waters (or epilimnion) will therefore record an increase in aquatic productivity as an increase in ()13c. (ii) RespirationlDecay. Organic (plant) material living in the surface waters eventually dies and sinks. At depth, this organic matter decays, releasing 12C-enriched CO2 back into the water, reducing the ()13C value of the DIe. Since Pamvotis is a shallow lake, this process is likely to be a relatively minor, though reasonably constant, factor (discussed further below). Carbonates precipitated at the bottom of the lake (or in the hypolimnion) will therefore record an increase in aquatic productivity as a decrease in ()13C. (iii) Input. Since there is no fluvial input to the lake, only the isotopic composition of precipitation and groundwater need to be considered. The lake is fed by springs at the base of a karstic aquifer system; the dissolved carbonates in the groundwater are therefore likely to remain at fairly constant levels over long periods of time and so can largely be discounted. The contribution to DIC from precipitation is also likely to be a negligible factor. (iv) Exchange With Atmospheric CO2 , A longer residence time of lake water will permit more gaseous exchange, resulting in more positive values of () l3c. The converse applies if the residence time is decreased. If groundwater, precipitation input and respiration/decay are all likely to be reasonably constant factors affecting the ()13C of the lake system, then either aquatic productivity or CO2 exchange remain the prime candidates for the dominant controlling influence on ()13e. As explained above, an increase in surface water productivity produces a more positive ()13C signal in carbonates precipitated in surface waters. During the Eemian, increased temperatures and precipitation would have encouraged increased levels of aquatic productivity (broadly reflected in the carbonate curve over this interval [section INTERPRETATIONS AND SYNTHESIS. 168 4.2.1]). However, the trend in ol3C over this interval is markedly negative, which would rule out a controlling influence by surface water productivity. If the carbonates being measured had been precipitated on the surface of (or within) the lake sediments, then a negative shift in ol3C would reflect increased respiration/decay, which is linked directly to surface water productivity (as described above). However, this is unlikely because of the physio-chemical factors affecting calcite saturation. Primary carbonates tend to be precipitated in surface waters (rather than at depth) because calcite saturation is linked to the solubility of CO2, which is temperature and pressure dependent (Dean, 1981). Increasing temperature or decreasing pressure decreases the solubility of CO2, the removal of which leads to calcite precipitation. In addition, the solubility of calcite itself is also temperature and pressure dependent (Kelts and Hsti, 1978). Other factors influencing calcite saturation and precipitation are discussed in Kelts and Hsti (1978) and Dean (1981). On the other hand, precipitation due to the oversaturation associated with loss of CO2 or bicarbonate during photosynthesis (i.e. biogenic carbonates) can occur anywhere within the photic zone. However, if conditions during the last interglacial were in any way similar to those prevalent today, thick algal material in the surface waters would have made the water very turbid, limiting the effective depth of this zone (see modern sampling data in appendix A). The negative trend in ol3C across this interval is therefore unlikely to be due to the carbonates precipitating on the bottom of the lake. Consideration must therefore be given to the exchange of CO2 with the atmosphere. Longer residence times will allow the lake waters to develop an evaporative signal, resulting in raised ol3C values. If the residence time is reduced, the waters have less opportunity to exchange with the atmosphere and so cannot develop such a strong evaporative signal. During the Eemian, the 0180 curve indicates that it was a time of high PIE relative to the preceding glacial phase (also supported by pollen data). This would result in a relatively more negative ol3C signal than during, for example, the previous glacial, when according to the 0180 record, evaporation rather than precipitation was more important. This interpretation can be supported by considering the magnitude of the isotopic values concerned. The isotopic fractionation between the 013C of bicarbonate and that of atmospheric CO2 is around +9%0 at 18°C. If Eemian CO2 levels are assumed to be between -7 to -6%0 (modern day values are approximately -8%0), then carbonate precipitating in equilibrium with the atmosphere would have a 013C value of between +2 to +3%0. This is close to the values seen at the beginning of the sampled interval INTERPRETATIONS AND SYNTHESIS • 169 (interpreted as MIS-6) and at the end (interpreted as MIS-5d). These two periods are known to have been cold and relatively arid, which suggests low levels of input to the lake by precipitation and from springs (i.e. a low PIE). Since the ()13C of the carbonate precipitating during these times was approximately in equilibrium with the atmosphere, this confirms longer residence times. Values of ()13C for the bulk of the Eemian were much lower however, averaging around -1%0. This suggests much shorter residence times (i.e. less opportunity to exchange with the atmosphere), in accordance with the high PIE indicated by the ()ISO record. Modern values of ()13C average around -4%0 whereas Eemian ()13C values average around -1 %0. This is a substantial difference if present day conditions are to be used as a basis for comparisons. The discrepancy can partly be explained by the fact that in the Eemian, lake-level was undoubtedly higher than in today's artificially-drained lake. Molluscan evidence presented above (section 7.3.1) clearly shows that the lake began to shallow after the end of the Eemian and never regained its former depth, even during the Holocene (this assertion is also supported by lithological evidence). A deeper lake would permit relatively longer residence times than in a shallower lake, explaining why the Eemian ()13C values are more positive than modern values. 7.4.3 Ostracod Shell Chemistry Stable oxygen and carbon isotopic measurements were carried out on shells of the ostracod Candona pennanenta at 20cm intervals over the top 25m of the core. Before any interpretation of the isotopic data can be suggested, the primary influences controlling the ()ISO and ()13C of the ostracods must be discussed. (a) Oxygen The controls on ()ISO in ostracod shell calcite in a shallow lake are effectively the same as for primary precipitated calcite (section 7.4.2, above), once biological factors such as 'vital effects' are taken into account (discussed below). Essentially, these controls are the temperature of calcite precipitation (i.e. water temperature) and the ()I SO of the lake water (which may in turn be influenced by the PIE ratio as well as the isotopic composition of precipitation and inflowing groundwaters). Following the same arguments outlined for primary carbonates, the ()ISO of carbonates formed in a shallow lake, such as Pamvotis, is most likely to be influenced by water temperature and the PIE ratio, particularly as the thermocline is not very pronounced (Overbeck, 1980). Other INTERPRETATIONS ' AND SYNTHESIS. 170 factors, such as the isotopic composition of precipitation and groundwater, are likely to remain relatively constant. The main control on ()ISO for the primary precipitated carbonates in Lake Pamvotis was thought to be the PIE ratio. If this factor is also the most important for the top 25m of sediment, then more positive ()ISO values denote a low PIE ratio. The ()ISO curve shown in fig. 4.10 shows more positive values at the base of the profile (-25m), at around 16m and again at about 10m, suggesting that these periods were relatively dry. This corresponds well with dry phases suggested by the age model and discussed at length in section 7.5, below. This interpretation also makes sense from the point of view of the magnitude of the ()ISO values. As explained above (section 7.4.2), using present-day climatic data, the range of ()ISO values for calcite forming in the lake is around -4.0%0 to -8%0, with the highest value of calcite precipitating from non-evaporated rain likely to be about -2.5%0 (T.H.E. Heaton, pers. comm.). However, this value will become more positive if the waters have undergone evaporation, as is the case with the modern waters (average ()ISO is around -1 %0). In addition, since ostracods do not always fractionate isotopes in equilibrium with their host waters, they often display species-specific offsets known as 'vital effects' (e.g. von Grafenstein et al., 1992). Xia et al. (l997b) recently used laboratory cultures of Candona rawsoni (a North American species) and estimated this offset to be around +1%0 (depending upon temperature). On the other hand, from an extensive (unpublished) collection of field data, U. von Grafenstein (pers. comm.) estimates that a more realistic estimate of offset for a variety of Candona species from central European lakes to be around +2%0. The ()ISO values obtained from this study are therefore well within the expected range (assuming that the waters have undergone a degree of evaporation), even making suitable allowances for the fact that modern climatic data were used. Once again, PIE appears to be the dominant influence on the ()ISO signal. (b) Carbon The ()I3C signal from ostracod shell calcite can sometimes be extremely difficult to interpret. Whilst ostracods are subject to similar controls on () 13C as primary precipitated carbonates (section 7.4.2, above), they have the 'added complication of living in a variety of different microhabitats and might therefore be subject to different isotopic influences. For example, in deep lakes, benthic epifaunal species may record different isotopic signatures to littoral or swimming species. The release of '2C-rich INTERPRETATIONS AND SYNTHESIS. l71 CO2 back into the DIC from respiration/decay of organic matter at depth will reduce the relative 8I3C value of the benthic ostracod shell calcite. On the other hand, littoral or swimming species in the epilimnion may record an enhanced 8 I3C value as photosynthesising phytoplankton take up 12C-rich CO2 from the DIe. Even if two species have shallow water ecological preferences, if one prefers muddy backwater areas amongst stagnant and decaying vegetation, whilst another prefers sandy and vegetation-free habitats, then the former will probably record a lower 813C signal than the latter, due to a local enhancement of 12C within the DIe. The ecology of Candona permanenta, the species used for isotopic determinations in this study, is discussed in section 6.3.2. It is likely to be a sublittoral epibenthic species, moving around over the substrate feeding on decaying organic matter in parts of the lake beyond the littoral zone. From the range of controls influencing 8 I3C composition, the most important is probably aquatic productivity, reflected in variations in respiration/decay of organic material at depth. This was regarded as a relatively minor factor when primary precipitated carbonates were considered (see above). However, it is likely to assume more importance when dealing with a benthic ostracod species that precipitates its shell carbonate whilst living on the floor of the lake. If 8 I3C is primarily controlled by respiration/decay, the curve might be expected to covary with 81 80, since increased precipitation (at a time when temperatures are also known to have increased) would result in increased surface water productivity (and hence increased decay at depth). In fact, for the lower part of the sequence (up to -ISm) the two curves only covary moderately (r = 0.31 for the smoothed data), indicating that perhaps respiration/decay was not such a dominant factor through this interval and other influences (such as variations in input from groundwaters or exchange with atmospheric CO2) had increased importance. However, covariance is stronger through the upper part of the sequence (r = 0.75 for the smoothed data), a period interpreted as the Holocene (section 5.8). This may indicate that respiration/decay became the dominant factor controlling 813C through this interval. For primary precipitated carbonate, it was thought that 8 13C was mainly controlled by exchange with atmospheric CO2, This resulted in a more positive values during cold stages, where less precipitation and longer residence times would allow the waters to develop an evaporated 813C signal. This is a trend that would be indistinguishable from respiration/decay, since drier climatic phases would result in longer residence times (more positive 813C values) and a lowering of aquatic productivity (less material to decay at depth, so more positive 813C values). In deeper lakes, benthic ostracods might be expected to respond more to respiration/decay rather than exchange with atmospheric INTERPRETATIONS AND SYNTHESIS. 172 CO2 (which would have more of an effect in the surface waters). In a shallow lake like Pamvotis, however, the signals are likely to be indistinguishable unless independent indications exists to support the influence of one control over another. Whilst mollusc an and lithological evidence (sections 7.3.1 and 4.1.1) suggest that the lake became progressively shallower over this interval, there is no independent evidence to suggest that productivity levels varied. Carbonate is thought to be an unreliable proxy for aquatic productivity over this interval (section 7.2.1). In addition, although the upper levels of the core are richer in faunal material than lower intervals, this may simply be a reflection of the deposition site being located in progressively shallower water, rather than an indication that productivity of the lake as a whole was increasing. As a result, it is difficult to determine exactly which control (if any) is the more dominant throughout this interval of core. As this particular ostracod is an epibenthic sublittoral species, it seems probable that the controlling factor is most likely to be respiration/decay, but this is difficult to justify. These interpretations are discussed further in section 7.5. One final point to make concerning the ostracod isotope results is that of seasonality. Studies have shown that most species of Candona moult only at certain times of the year when conditions are optimal (e.g. Xia et al., 1997a). By means of extensive field sampling in Lake Ammersee in Bavaria, von Grafenstein (1992) has found that many species of Candona display a frequency maximum of adults during autumn and early winter. This means that the isotope signals derived from these species will carry a seasonal bias. Central European climate is different to that of the Eastern Mediterranean and little is known about the preferences and tolerances of those ostracod species found only in Balkan lakes. It is possible that the data from Ioannina also shows an autumn/early winter bias. However, without detailed ecological and population studies on C. permanenta, it is difficult to support such an assertion. 7.4.4 Open or Closed Lake System? Hydrologically closed lake basins are known to be sensitive to climatic variability, since their volume and chemistry are influenced primarily by PIE. Lake Pamvotis is a shallow lake with no pelmanent outflow, suggesting that it may be a closed system. If this were the case throughout its history, then much of the chemical and isotopic variability noted in the record can be interpreted as resulting primarily from climatic INTERPRETATIONS AND SYNTHESIS. 173 influences. However, as discussed in section 2.5, the lake is part of a karstic aquifer system underlying the Mitsikeli ridge. In addition, the blocked sink-holes (katavothrae) in the floor of the lake can become temporarily cleared (for example, by tectonic activity), inducing a lake-level drop that is not a result of climatic influences. The chemical signature of lake waters can sometimes be indicative of the 'open' or 'closed' status of a lake basin. Talbot (1990) suggests that a covariance of r> 0.7 between 8180 and 813C of primary lacustrine carbonates indicates that they were precipitated in a hydrologic ally closed system. However, he also points out that several open lakes have covariances close to those of closed lakes. These include Lobsigensee in Switzerland (r = 0.65) (Siegenthaler and Eicher, 1986) and Little Lake in Ontario, Canada (r = 0.51) (Turner et al., 1983). Talbot (1990) argues that this is probably because, like closed lake systems, they have relatively long residence times. In addition, von Grafenstein (pers. comm.) advocates extreme caution when assessing the significance of covariant stable isotopic data from lake systems. His detailed (unpublished) 8180 and 813C measurements from Lake Ammersee in Bavaria show a strong covariance (r> 0.9), but the basin is demonstrably open. He attributes these results to the importance of PIE for this particular lake system and stresses the danger in the automatic classification of open/closed lakes based solely on isotopic evidence. The chemical results obtained from the modem Ioannina lake waters and fossil carbonates will now be considered in turn. (a) Modern The covariance between the 8180 and 8 13C values of the modem lake waters (fig. 4.9) is reasonably strong (r = 0.91), suggesting that it may be effectively closed. The evaporative trajectOlY of the Ioannina waters also helps to support this suggestion (fig. 4.8). Its gradient of 4.8 is close to the value of 5 that Faure (1986) considers indicative of closed lake basins. (b) Last glacial - Holocene The isotopic signals from ostracods were measured over this interval (section 4.2.3). As explained previously (section 7.4.3), ostracod shell calcite precipitated in shallow lakes behaves like primarily precipitated calcite, once biological factors such as 'vital effects' have been accounted for. Overall covariance between values of 8180 and 813C derived from ostracod shells over this interval is only moderate (r = 0.54, smoothed INTERPRETATIONS AND SYNTHESIS • l74 data). However, covariance varies between different parts of the record (fig. 4.11). Below ISm the curves covary with an r-value of 0.31; above ISm, the r-value improves to 0.75. This may be a reflection of the changing influence of other factors on the isotopic composition of the waters from which the ostracods build their shells, for example the changing trophic status of the lake in response to climatic variation. A more likely alternative is that it represents an increase in organic productivity caused by lake-level fluctuations (discussed in section 7.5, below). (c) Eemian An isotopic signal derived from bulk sediment carbonate was measured over this interval (section 4.2.1). The 0180 and oI3e values covaried reasonably well (r = 0.58). Again, the fact that ol3e does not covary even more closely with 0180 probably indicates that other hydrological factors were also significant, though to a lesser degree. (d) Discussion Until a detailed hydrological study is carried out on the modem lake, any interpretation of the data has to be viewed with a degree of caution. It is difficult to classify the hydrological status' of the modem Lake Pamvotis as either entirely open or entirely closed, since in reality, it probably falls somewhere in between. In general terms, however, the isotopic values show that the surface water has a residence time sufficient enough to permit some evaporation, which may be broadly indicative of 'closed' status (agreeing with the blocked katavothrae hypothesis previously outlined). In palaeolake terms, it is again difficult to assess clearly the hydrological status of the lake. Although the covariances between 0180 and ol3e values do not unequivocably fall into the closed-basin category of Talbot (1990), they are reasonably close. However, they celtainly support the probability of long residence times and the important influence of PIE on lake-level indicated by the isotopic curves for both the Last glacial - Holocene and Eemian intervals. In summruy, the available data therefore suggest that Lake Pamvotis can be considered in the broadest telIDS to be a closed hydrological system. Modem and fossil isotopic results indicate long residence times and the importance of PIE on lake-level variability. Nevertheless, other hydrological factors ru'e also likely to be important and further INTERPRETATIONS AND SYNTHESIS • 175 detailed work is necessary (particularly on understanding the complexities of the modem lake system) before they can be adequately accounted for. 7.5 SYNTHESIS This section represents an attempt to link together the data presented in the previous chapters and, bearing in mind some of the interpretations discussed above, derive a coherent and comprehensive palaeoenvironmental history of the lake. Particular attention is paid to those intervals of the core studied in higher resolution. Core 284 does not extend back to bedrock, making it impossible to derive any conclusions concerning the origins of the lake. The 284 record begins somewhere in MIS-16, approximately 600ka ago. The borehole site was situated in part of a deep (perhaps the deepest) sub-basin within the lake. Ostracod faunal evidence (and lack of molluscan shell material) suggests that the site was probably profundal and remained so for much of its history, although it is difficult to estimate an absolute value for the water depth. Sediments accumulated reasonably rapidly on the floor of the lake, a process that was aided by the continual subsidence of the sub-basin. The sediments consisted of primarily precipitated calcite, siliceous material (largely diatomaceous), aeolian material (derived originally from the deserts of North Africa) and clay minerals, ultimately derived from the weathering of the catchment (particularly, the nearby flysch deposits). Pedogenic enhancement of the catchment soils (on both limestone and flysch units) provided magnetic minerals that were eventually washed into the lake and incorporated into the sediments. The productivity of the lake appears to have fluctuated over time in response to climatic variation, in tandem with the variability in vegetation communities within the catchment (Tzedakis, 1991 , 1993, 1994) (see also the discussion of leads/lags, below). Warmer, interglacial periods were characterised by high PIE, a forest succession and increased primary calcite precipitation linked to a rise in aquatic productivity. Glacial periods saw low PIE, a corresponding expansion of open vegetation communities and lower levels of calcite precipitation. Extended severe climatic conditions during the penultimate glaciation (MIS-6) led to a gradual lowering of the lake-level. Aquatic molluscs, which are nOlmally mainly preserved in littoral or sub-littoral sediments, appeared in the record as the site of the 284 borehole became shallower. INTERPRETATIONS AND SYNTHESIS. 176 7.5.1 Eemian According to the age model, the interval 83-100m is thought to include the whole of the Eemian. The beginning and the end of the last interglacial in core 284 is well constrained both palaeomagnetically and by means of U-series determinations (chapter 5). The vegetational history from core 249 suggests that the last interglacial period (designated as the Metsovon interglacial at Ioannina) was characterised by a significant increase in open forest taxa, dominantly Quercus, along with Ulmus, Zelkova and Olea (Tzedakis, 1991). This was succeeded by a Carpinus-dominated forest, in which Abies also became important at higher altitudes. A second expansion of Quercus-dominated forest followed, with the final phase of this period being marked by the appearance of Pinus and Betula, accompanied by a slight decrease in forest cover. This was interpreted by Tzedakis (1991) as indicative of warm, 'Mediterranean' conditions, followed by an increase in moisture availability. Unpublished high resolution pollen analysis at 20cm intervals through this period of 284 (appendix C, courtesy of P.e. Tzedakis) confilms this vegetational succession. Quercus frequencies increase markedly just below 96m, followed by an expansion of Mediterranean evergreen elements. Carpinus values reach a maximum at about 93m. The other main features of the Metsovon interglacial are present (such as the second increase in Quercus and Pinus, with Betula achieving more importance towards the end of the interglacial), but with considerably more detail. This is now discussed in conjunction with the other proxies analysed through this interval. A comparison of the stable isotope measurements, carbonate and organic matter content, magnetic susceptibility and selected pollen data is illustrated in fig.7 .2. A summary pollen diagram for this interval is presented in appendix e. As in section 4.2.1, the plot is split into arbitrary zones for the purposes of description. The contribution that this sequence offers to the debate concerning climatic variability within the Eemian is discussed further in section 8.5.1. 100-98.5m The end of the penultimate glaciation appears to have been a time of unstable climate. Several indicators show distinct variations across this interval. The values of (5 180 oscillate around -3.5%0, although the overall trend is progressively negative. This suggests that the PIE ratio during this time was not entirely stable and that the arid (low PIE) conditions at the end of the glacial. phase were gradually becoming wetter. Over the same interval, (5I3C values also vary in the same way, with a positive oscillation occurring at the same time as in the oxygen record (-99.5m). This suggests that the residence time of the lake waters was probably changing in response g ..c Q.. Q,) Cl Organic Matter Content (%) oI3 C (%0) AP (%) o 5 10 15 20 -2 -I 0 I 2 3 4 o 20 40 60 80 100 83 ] .~ I·S 7 ~ :;; ~ "-<:; )' [ 84 ; ~ 85 86 87 88 89 90 91 92 93 94 95 96 97 98 99 100 101 102 > ~ \ ,~ ,< o 10 20 30 Carbonate Content (%) 40 -I 0 2 3 Magnetic susceptibility (x!()7 m3kg- l ) 4 -7 -6 -5 -4 8, 80 (%0) -3 -2 o 500000 Pollen Concentration (grains crrr3) Fig. 7.2 Summary plot covering Eemian section of core. Pollen concentration and AP% curves from Tzedakis (unpubl. data) . See text for zonation scheme. 83 84 85 86 87 88 89 90 91 92 93 94 95 96 97 98 99 100 101 102 g ..c Q.. Q,) Cl ~ ~ :::tl ;g ~ ~ ::j a ~ ~ ~ V:l ~ ~ ~ • -.l -.l INTERPRETATIONS AND SYNTHESIS. 178 to the variablility in PIE. Total carbonate content also varies in the same way as the isotopes, with a matching positive oscillation, perhaps indicative of variable productivity levels. The vegetation record (appendix C) shows a small increase in arboreal pollen (especially Quercus, Carpinus and Corylus) and a slight decline in grasses and Artemisia. This confirms that the open vegetation conditions prevalent during the penultimate glaciation were coming to an end. 98.5-96.0m This zone is characterised by marked variability in all indicators. Both the oxygen and carbon isotope values oscillate sharply, beginning with a major negative excursion, followed by a positive excursion of almost the same amplitude and then a slight negative shift at the very end of the zone. In fact, the 81BO values undergo a subdued second oscillation at the end of the zone, which is not reflected velY well in the 8 I3C record. However, it is seen (as an inverse relationship) in the total carbonate curve, which itself records the whole oscillation. These data suggest that an initial increase in PIE at the beginning of the interval suddenly undergoes at least one, or possibly two oscillations before the end of the zone. This variability at the beginning of the Eemian has been noted in other high-resolution sequences, for example, the un smoothed curve of marine core V19-30 (Shackleton et al., 1983), a Danish foraminiferal and isotopic record (Seidenkrantz, 1993) and Norwegian speleothem records (Lauritzen, 1990; 1995). The oscillation has now been termed the Zeifen­ Kattegat Oscillation (ZKO) after the warm Zeifen interstadial (first recognised from Zeifen in southern Germany) and the Kattegat stadial (first recognised from the Anholt IT borehole from Denmark) (Seidenkrantz et al., 1996). The ZKO also manifests itself in the vegetation record from 284 over this interval, with a resurgence of grasses and a peak in the alga Pediastrum (appendix C). 96.0-90.90m Values of 8I3c remain at a fairly constant level throughout (around -0.8%0), whereas values of 81BO gradually decrease by approximately 0.3%0. Carbonate content is slightly more variable, averaging around 20%, whereas magnetic susceptibility is reduced across the entire interval. These data suggest that this was a relatively stable period, with conditions of high PIE and productivity being maintained throughout. The complete absence of molluscan fragments and the low abundances of ostracods suggests relatively deep lake-levels. This zone is interpreted as the establishment of full, stable Eemian conditions, a conclusion supported by the pollen signal (appendix C). The APINAP curve stabilises and the vegetational succession is characterised by the rise in Quercus (deciduous and evergreen), Carpinus, Osttya, Abies, Alnus and other taxa at the expense of Artemisia, grasses and chenopods. INTERPRETATIONS AND SYNTHESIS. 179 90.90-86.10m A fall in 8 13C at the beginning of the zone is mirrored by a fall in 8180, albeit slightly delayed. Values of 8 13C rise slightly during the rest of the interval, only falling slightly at the velY end of the zone. Values of 8180 remain fairly constant (around -5%0), although the very end of the zone sees a fall (again, slightly lagging behind the 8 13C). Both curves record a distinct drop at 88m (but just over a single point). The fact that this is not obviously reflected in any of the other indicators suggests that it is a spurious point, probably related to errors derived from preparation or measurement procedures. Carbonate content varies markedly over the entire interval, with a noticeable positive oscillation towards the end of the zone. Magnetic susceptibility increases marginally at the beginning of this interval. These data suggest that this was a period of increasing instability. The decrease in 8180 suggests slightly wetter conditions (higher PIE), athough it is accompanied by an increase in 8 13C, suggesting that residence times were increasing. This apparently anomalous situation can be explained if seasonal factors (for example, wetter winters and drier summers) became more important, possibly accompanied by a slight drop in temperatures. Faunal evidence suggests that the lake-level was shallowing gradually (an increase in sub-littoral Candona ostracod species is seen), also confirmed by the increase in 8 13c. The oscillations of the carbonate curve are interesting, particularly as the magnitude of the variablity is not reflected as clearly in most of the other indicators. However, a drop in carbonate content does coincide with the decrease in 813C at the end of the zone. This probably indicates a slightly higher lake-level, rendering the site of 284 once more too deep for many of the benthic ostracods that contribute to the overall carbonate content of the sediment. The pollen record also suggests that conditions were becoming slightly cooler and more variable over this interval, patticularly noticeable in the APINAP curve (fig. 7.2 and appendix C). Artemisia, grasses and chenopods all increase gradually and Betula reappears. Carpinus, Ulmus and Ostrya on the other hand, all decline. 86.10-83.0m This final zone sees a return to the extreme variability seen at the beginning of the sampled interval. Above 84m, marked (though irregular) increases are seen in values of 813C and 8 180 to values compat'able to those recorded at the end of MIS-6. This is accompanied by a rise in magnetic susceptibility and distinct crashes in the carbonate content and the APINAP curve. Data suggest an inegular resumption of cool and dry stadial conditions, confirmed in the pollen record by oscillations in the APINAP values (fig. 7.2 and appendix C). INTERPRETATIONS AND SYNTHESIS. 180 7.5.2 MIS-5d - Last Glacial Maximum The period stretching from the end of the Eemian (approximately 116ka) to the LGM (approximately 20ka) has not been studied in detail during this study. Nevertheless, some meaningful comments can still be made. In common with evidence derived from long European pollen sequences, ice cores and the marine oxygen isotope record (all discussed at length in chapter 8), the Ioannina sequence displays distinct variability over this interval (see also the review by van Andel and Tzedakis, 1996). The carbonate curve oscillates several times (between approximately 5-10%) suggesting variable levels of productivity, although this is likely to be influenced by the re-appearance of molluscan material in the sediment above about 70m. The molluscan faunal evidence itself suggests an oscillating lake-level, but with an overall trend towards shall owing. Above about 45m, occasional beds of the freshwater mussel Dreissena appear in the record, indicating very shallow lake-levels (probably in the order of a few metres). These culminate in substantial shell beds at around 26m, coinciding with the part of the record interpreted by the age model as representing the LGM. Conditions at Ioannina during this time inferred from pollen data were thought to have been distinctly cold and arid, with average summer and winter temperatures as much as 10°C lower than present-day (Bottema, 1974; Vita-Finzi, 1978). The Ioannina 249 pollen record suggests a desert-steppe environment, the vegetation being dominated by open, discontinuous grasses and Artemisia (Tzedakis, 1991, 1994). 7.5.3 Last Glacial - Holocene Transition Detailed isotopic and faunal analyses were carried out over the top 25m of the core, interpreted by the age model to extend from the end of the last glacial period, through the Lateglacial and into the Holocene. Isotopic measurements were derived from ostracod shells at 20cm intervals, carbonate and organic content was measured every lOcm and magnetic susceptibility was measured every 1m (fig 7.3). Radiocarbon determinations (section 5.3) also helped to constrain the chronology for this section of core. 25.0-16.80m Values of carbonate content and organic matter both increase slightly above about 23.50m, after which the organic matter remains at a relatively constant level, whereas the carbonate content fluctuates and begins to rise at the end of the zone. 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Views of adult Planorbarius comeus. Views of Dreissena (Carinodreissena) cf. stankovici. Carina clearly visible on fig. E. 11 , I c 1 cm B F E H 1 cm 1 cm PLATE 11 PLATE III A-C Juvenile specimens of Bithynia graeca. D Damaged adult specimen of Bithynia graeca. E Operculum from adult Bithynia graeca. F-G Detail of reflected lip from adult Bithynia graeca. H-L Views of adult and juvenile specimens of Gyraulus janinensis. M Detail of spiral sculpture from Gyraulus janinensis. .j ------- A-E F G-H PLATE IV External, internal and dorsal views of adult and juvenile specimens of Cyprideis torosa. External view of adult specimen of /lyocypris bradyi. External and internal views of /lyocypris slavonica. A-B C-D E-F G-H PLATE V External and internal views of adult female specimen of Candona permanenta. External and internal VIews of adult male specImen of Candona permanenta. External and internal VIews of adult specImens of Candona cf. dedelica. External and internal VIews of adult specImens of Candona cf. parvula. A-C D-E F-G PLATE VI External, internal and dorsal views of adult specImens of Leptocythere cf. ostrovskensis. External and internal views of specimens of Heterocypris rotundatus. External and internal views of adult specimens of Prionocypris sp. PLATE VII A-B External and dorsal views of adult specimens of Cypridopsis vidua. c External view of adult specimen of Paralimnocythere cf. compressa. D External view of adult specimen of Eucypris virens. E External view of adult specimen of Cypria ophtalmica. F External view of adult specimen of Darwinula stevensoni. APPENDICES APPENDIX A SAMPLE SITE DETAILS Unless otherwise stated, the weather at sampling points was clear and hot both prior to and at the time of sampling. Turbidity was measured using a l00mrn white disc, noting the depth at which it could no longer be seen. Sample site locations are illustrated in fig. 3.1. SITE 1 Limnopoula, adjacent to KEKOP centre Sampled: 13/9/94 Time: 08.10 Shallow, rocky shoreline Some sparse aquatic broadleaf vegetation. Algal covering on water surface. Rubbish and debris from human activity. Water depth at sample point: Turbidity: Water temperature: pH: Dissolved oxygen: Alkalinity: Conductivity : 0.23m 0.30m 12.2°C 7.53 6.1mg/l 120mg/l 332JlS SITE 2 NE shore of lake in 'backwater' area Sampled: 13/9/94 Time: 18.45 Grassy banked steeply dipping shoreline adjacent to substantial reed-beds. Used by cattle, goats, sheep etc. for drinking and grazing. Tenestrial vegetation dominantly grass, a few shrubs. Aquatic vegetation included floating broadleaf, some reeds, algal covering. Water depth at sample point: Turbidity: Water temperature: pH: Dissolved oxygen: Alkalinity: Conductivity: 0.28m 0.18m 28.3 °C 7.48 6.3mg/l 120mg/l 359JlS APPENDIX A SITE 3 NW of Site 2 along lake road, approx 500m Sampled: 15/9/94 Time: 09.15 Marshy, muddy reed-beds. Used by cattle, sheep goats, etc. as drinking place. Terrestrial vegetation limited to grass. Aquatic vegetation dominantly reeds and grasses, substantial algal slime. Water depth at sample point: Turbidity: Water temperature: pH: Dissolved oxygen: Alkalinity: Conductivity: 0.18m 0.22m 21.TC 7.77 0.8mg/l 224mg/1 44511S SITE 4 NNW of Katsikas at lake edge Sampled: 15/9/94 Time: 10.55 Low-lying grass area, surrounded by reed-beds. Terrestrial vegetation limited to grass. Aquatic vegetation dominantly floating broadleaf (lily), amidst some grass and reeds. Water depth at sample point: Turbidity: Water temperature: pH: Dissolved oxygen: Alkalinity: Conductivity : 0.15m 0.13m 19.TC 7.42 9.5mg/l 212mg/l 33411S SITE 5 NW of Katsikas, sandy shore of channel to pumping station Sampled: 15/9/94 Time: 18.45 Sandy shoreline, fairly steeply dipping. Ten'estrial vegetation entirely short grass. Minimal aquatic vegetation, a little floating algae (likely channel cleared regularly). Used by cattle etc. Much human rubbish and debris nearby. Water depth at sample point: Turbidity: Water temperature: pH: Dissolved oxygen: Alkalinity: Conductivity: 0.22m O.13m 20.9°C 7.53 11.1mg/l 149mg/1 32311S • I '. APPENDIX A SITE 6 Between Arnfithea and Perama on grassy 'breakwater' road, close to inlet stream Sampled: 16/9/94 Time: 17.55 Steeply dipping shore from artificial roadway, grassy and reed-covered. Terrestrial vegetation dominantly grass. vegetation. Water depth at sample point: 0.18m 0.22m 13.3°C 7.64 1.lmg/l 217mg/l 679~S Turbidity: Water temperature: pH: Dissolved oxygen: Alkalinity: Conductivity: SITE 7 Nissi Island, southern side Sampled: 17/9/94 Time: 09.35 Reeds and grasses dominate aquatic Shallow, rocky shoreline encroaching onto muddy flats fringed by extensive reed-beds. Much aquatic broadleaf vegetation. Algal covering on water surface. Rubbish and debris from human activity. Used by sheep etc. Water depth at sample point: Turbidity: Water temperature: pH: Dissolved oxygen: Alkalinity: Conducti vity: SITE 8 Nissi Island, SE tip 0.18m 0.24m 15.5°C 7.83 1.5mg/l 295mg/l 603~S Sampled: 17/9/94 Time: 11.35 Shallow, rocky shoreline Little terrestrial or aquatic vegetation. Thick green algal covering on water surface. Rubbish and debris from human activity. Water depth at sample point: Turbidity: Water temperature: pH: Dissolved oxygen: Alkalinity: Conductivity: 0.24m 0.03m 21.5°C 7.53 6.4mg/l 127mg/l 332~S SITE 9 North of Island, on disused car-ferry platform Sampled: 17/9/94 Time: 19.25 Metal platform in channel cut through reed-beds. Some floating broadleaf; reeds and grasses adjacent. Water depth at sample point: 0.15m 0.28m 24.1°C 7.72 9.3mg/1 135mg/1 3341lS Turbidity: Water temperature: pH: Dissolved oxygen: Alkalinity: Conductivity: SITE 10 Shoreline SE of Ioannina town. Sampled: 18/9/94 Time: 10.50 Shallow, flat-lying mud / grassy area. APPENDIX A Abundant floating broadleaf (lily). Thick algal covering on water surface. Rubbish and debris from human activity. Water depth at sample point: 0.24m 0.08m 13.0°C 8.09 12.9mg/1 151mg/1 340llS Turbidity: Water temperature: pH: Dissolved oxygen: Alkalinity: Conductivity: SITE 11 Eastern extent of lake, channel cut through reeds to pumping station. Sampled: 19/9/94 Time: 10.25 Steep muddy shore. Some sparse floating broadleaf. Algal covering to water surface. Water depth at sample point: 0.17m 0.15m 23.1 °C 7.54 1O.2mg/l 172mg/1 3371lS Turbidity: Water temperature: pH: Dissolved oxygen: Alkalinity: Conducti vity: .' ," -' , . Parameter SITE SITE SITE SITE SITE SITE SITE SITE SITE SITE SITE (mg/l) 1 2 3 4 5 6 7 8 9 10 11 Zn 0.008 0.011 0.003 b.d. 0.001 b.d. 0.001 0.005 b.d. b.d. 0.001 Pb b.d. 0.054 b.d. 0.035 b.d. 0.001 0.003 0.012 0.011 0.038 0.047 Cd 0.006 0.007 0 b.d. b.d. b.d. b.d. 0.002 0.001 0.003 0.004 Si 4.872 7.36 8.895 5.482 5.893 4.554 10.42 5.296 5.874 5.123 5.672 Mn 0.011 0.096 0.092 0.028 0.026 0.015 0.097 0.015 0.069 0.032 0.015 Fe b.d. 0.028 0.613 b.d. b.d. 0.012 1.421 b.d. 0.063 b.d. b.d. Mg 10.37 10.38 10.39 9.989 10.06 5.387 14.21 10.11 10.3 10.01 10.14 Al 0.029 0.037 0.002 0.026 0.024 0.026 0.041 0.032 0.015 0.04 0.024 V 0.009 0.01 0.003 0.004 0.007 0.014 0.008 0.016 0.014 O.oI1 0.017 Ca 38.76 44.02 52.78 40 39.81 70.37 90.7 40.2 41.23 39 39.57 Cu 0.002 0.007 0.009 0.008 0.007 0.005 0.008 0.004 0.009 0.003 0.009 Sr 0.214 0.226 0.245 0.212 0.216 0.324 0.4 16 0.219 0.219 0.212 0.218 Na 19.77 20.01 20.72 19.74 19.67 57.93 25.26 19.08 19.33 18.94 19.44 K 3.492 3.431 3.072 3.366 3.505 0.602 1.638 3.461 3.444 3.479 3.279 Nitrate 0.8 0 .9 1.6 1.4 1.7 0.6 -0.3 1.5 1.3 1.8 1.9 Sulphate 0.76 1.02 1.27 1.27 0.95 28.86 7.44 2.03 0.95 1.59 2.61 Silica 10.4 15.8 19.0 12.5 12.6 9.7 22.3 11.3 12.57 11.0 12.1 Phosphate 8.1 0.7 0.7 1.6 1.3 0.6 0.8 2 1.1 1.3 1.1 Chloride 29 23 27 21 28 100 37 24 23 23 26 Alkalinity 146.5 146.5 273.4 258 .7 181.8 264.8 360.0 155.0 164.8 184.3 209.9 . Dissolved Oxygen 6.1 6.3 0.8 9.5 11.1 1.1 1.5 6.4 9.3 12.9 10.2 a Tempe¥ure (QC) 15.6 15.8 16.9 15.8 15.8 15.6 17.7 15.6 18.5 15.6 15.5 pH 7 .53 7.48 7.77 7.42 7.53 7.64 7.83 7.53 7.72 8.09 7.54 Conductivity V"S) 332 359 445 334 323 679 603 332 334 340 337 Salinity (%0) 0.268 0.266 0.41 0.369 0.299 0.539 0.561 0.269 0.278 0.294 0.326 Charge Balance Error (%) 2.94 11.26 7.55 11.96 1.05 8.43 1.46 5.16 5.09 0.94 6.05 Appendix B. Modern water chemistry data. Salinity calculated from Total Dissolved Solids (TDS). b.d. = below detection. Mg/Ca ratio = 0.34. lOAN 284 A\' ' 0" 0<:' Depth m 84 85 86 87 88 89 90 91 92 93 94 95 96 97 98 99 100 ~"" .~0 " )"~' If"'" «/0,,0 0<:- .,~"" ,'li (j'l>~ ~"" 'li'Ci, 1 ~v ~ « ~ ,," \'1> 0'1> ",,'I> ,," eI" 'I> ,'I>G .~4,~ "". ~v cA'I> ',<:' OV 0,0 'I> Cp