Marelac Ugent – Lacustrine Systems April 2005 H. Eggermont Brief summary: Limnology and paleolimnology of African lakes Part I: Limnology of African lakes Location: Between latitude 37°N and 35°S Climate: The main determinant of tropical weather variability is the annual north-south migration of the ITCZ and associated monsoonal wind systems which advect moisture from the tropical oceans to the hot adjacent continents. There are two rain seasons in tropical Africa (MarchMay = long rains; October-December = short rains). Most of the precipitation during these periods is coming from the Indian Ocean and thus subjected to dynamic interaction between ocean, atmosphere and land in the Indian monsoon region. The Intertropical Convergence Zone (ITCZ) is an area of low pressure that forms where the Northeast Trade Winds meet the Southeast Trade Winds near the earth's equator. As these winds converge, moist air is forced upward. This causes water vapor to condense, or be "squeezed" out, as the air cools and rises, resulting in a band of heavy precipitation around the globe. This band moves seasonally, always being drawn toward the area of most intense solar heating, or warmest surface temperatures. It moves toward the Southern Hemisphere from September through February and reverses direction in preparation for Northern Hemisphere Summer that occurs in the middle of the calendar year. The result of ITCZ is not only seasonal wind patterns but also seasonal rainfall. Landscape – rift formation - Few folded mountain belts (Ruwenzori in East Africa, Draken’s mountains in South Africa, Atlas in North Africa, Tibesti mountains in central Sahara,…) - The Great Rift is an extension of mid-oceanic ridges. It extends southward from the Dead Sea through the Red Sea, coming ashore at Afar and passing through Ethiopia to split into two branches, the Western Rift from Lake Albert and Ruwenzori through Lake Tanganyika and beyong to Lake Malawi and Chilwa (through DR Congo, Uganda, Rwanda, Burundi, 1 Marelac Ugent – Lacustrine Systems April 2005 H. Eggermont Tanzania, Zambia and Malawi) – and the Eastern Rift from Lake Turkana to Basotu (through Kenya and Tanzania). - The Rift system of the Cameroon highlands (has also been important for the formation of lakes) Origin of lakes: - Tectonic lakes: The largest and deepest lakes were formed directly by tectonic activity (displacements of the earth’s crust). Such crustal activity has gone on intermittently since Precambrian time, but most of the conspicuous features of the present Rift have been formed by tectonic activity that began in the Miocene and continues to present day. Lakes Albert, Turkana (Rudolf), Tanganyika, Mweru and Malawi occupy basins formed by downthrust fault blocks (grabens, which are often long, narrow and deep; mainly between 8°N and 15°S). Lake Victoria, the largest lake of Africa and the world’s second largest freshwater lake is occupying a shallow depression between the shoulders of the West and East African Rift; it was formed by uplifting of the entire basin (=upwarping; such lakes are large and fairly shallow). There is little geological evidence for deciding which is the oldest of the tectonic lakes: without radiometric dating and paleontologic study of complete sections through their sediments, the ages of the lake basins and especially during which they have held water continuously, cannot be determined with assurance (Lake Tanganyika holds >1500 m of sediments, and Albert at least 1200 m). Many people believe that Tanganyika and Malawi are actually the oldest. - Lakes associated with volcanic activity: Volcanism associated with rifting has been a fertile source of African lakes. (1) Some lake districts, such as that of Kigezi in southwest Uganda, were formed mostly (but not exclusively) by lava damming of river valleys. Few of these lakes have been dated; Lake Kivu is the largest lava-dammed lake. (2) Other large and deep lakes occupy the craters of calderas (= collapsed or exploded volcanoes; basins formed by the subsidence of the roof of a partially emptied magmatic chamber, like Lake Empakai in Tanzania. (3) In several places, volcanic explosions, with or without the ejection of substantial amounts of volcanic ash, have created a large number of small (<2 km), round and often deep (>100 m) maar lakes (=explosion craters; some appear to be about 5000 years old). Maars result from lava coming into contact with groundwater or from degassing of magma. Maar regions include western Uganda (exceptionally diverse!!), Bishoftu crater lakes in Ethiopia, and several lakes in Tanzania and central Kenya. 2 Marelac Ugent – Lacustrine Systems April 2005 H. Eggermont - Lakes formed by glaciers and ice, such as on the higher (extinct) volcanoes (Mt Kenya) and also in the Ruwenzori mountains. Most of them are amphitheater-shaped (quite small and shallow) depressions caused by glaciers scouring glaciated valleys (=cirque lakes; paternoster lakes). Fiord lakes are absent, and moraine-dammed lakes are scarce (those that appear to be moraine-dammed are landslide-dammed or glacier-dammed instead). Most are formed during Pleistocene glaciation and more recently (unlikely that they are much older than 15000 years). During the Pleistocene, the tropical snowline did not as a rule extent below 3000 m, so most lakes in tropical mountains are to be found from 3000 m upwards. - Lakes formed by wind = deflation lakes, sometimes with accompanying erosion by wallowing mammals. Examples include saline playas in arid areas - Lakes in interdune hollows, the most spectacular being the lakes in northern Chad (Ounianga serir/kebir) - Lakes associated with shorelines, rivers… African rivers have the usual complement of oxbow ponds and cutoff channels - Man-made lakes (artificial lakes): series of very large man-made lakes is created since the late 1950s (Lake Volta is the world largest!) Non-nutrient chemistry Main chemical sources come from: (1) inflow and seepage, depending quantitatively and qualitatively upon the general hydrology and geochemical character of the catchment plus cultivation, fringing samps, human settlement etc. The waters in Subsaharan Africa are dominated to an unusual extent by ions derived from the incongruent solution of sodium silicate rocks, rather than ions derived from congruent solution1 of carbonates as in North America, Asia and especially Europe. There is also a strong tendency, accordingly, for most African waters, to be solutions of sodium bicarbonate (Na+, HCO3- and CO2-), rather than calcium bicarbonate. Many of them have accompanying pH of 10 or more. The typical chemistry of African lakes is in fact a combination of chemical peculiarities of the volcanic rocks that surround many of them, plus (!) evaporative concentration with selective removal of less soluble salts. incongruent solution: more soluble parts of the solid go into solution first, producing a solution and leaving solid residue with different composition 1 3 Marelac Ugent – Lacustrine Systems April 2005 H. Eggermont (2) atmospheric precipitation both wet and dry. E.g., near the sea coast, and in some cases inland, there is a considerable contribution of cyclic sea salt. (3) from gaseous exchange with the atmosphere. Gase exchange is determined by the mixing regime. Other factors playing a role here are e.g. layers (free-floating mats) of macrophytes widespread in both shallow and deeper waters include the species Pistia stratiotes, Eichhornia crassipes, and Salvinia molesta. Such mats can lead to reduced concentrations in the waters below (i.e., they can create particular barriers to vertical exchange) The chemical composition of African waters is largely controlled by rock weathering, evaporative concentration and precipitation of calciumcarbonate. Anions: Lakes are largely bicarbonate-carbonate (cf. alkalinity) dominated. Various studies show that carbonate-bicarbonate (and hence alkalinity), chloride and sulphate all increase regularly with increasing conductivity in African waters. Chloride-dominated waters are most strongly represented in coastal or near coastal situation with present or past ingress of seawater (lagoons in North and West Africa; coastal lakes, but also inland, like Lake Katwe, and Sahara salt lakes, like Dawada). Concentrations of fluoride can be very high! Perhaps our evolution in an environment where the natural waters are so fluoride-rich generated the anomalously high human requirement for this ion. In the wider world, we must supplement the fluoride content of our drinking water to develop sound caries-resistant teeth. Cations: In the commonest type, bicarbonate-carbonate, increase in salinity (or conductivity) is associated with a steady rise in the concentrations of Na+ rather less regular rise of K+, and final loss of precipitation of Ca2+ and Mg2+ (as carbonates). In fact, calcium and magnesium also increase linearly with conductivity, but only up to about 200 µS/cm and 1000 µS/cm, respectively. Precipication of calcium carbonates is easily documented; precipication of magnesium is less common. Precipication of sodium carbonates also exist e.g. Lake Magadi in Kenya supports an industry exploiting the trona of this lake. Thus the ratio of monovalent to divalent cations increases and in saline waters Na+ is dominant. West Rift lakes of the volcanic sources (Virunga volcanic field) are unusually rich in Mg2+ and K+. Concentration of salt is often generated by enhanced evaporation under dry conditions. The lake waters encompass virtually all of the very wide range of salinity. pH generally rises with increasing alkalinity, locally depressed by accumulation of CO2 and raised by active removal in photosynthesis. 4 Marelac Ugent – Lacustrine Systems April 2005 H. Eggermont ≠ Temperate lakes: The chemical composition is very different from that of temperate lakes where calcium and bicarbonate tend to dominate. Soda lakes Shallow soda lakes cover large areas of the Rift Valley in Ethiopia, Kenya and Tanzania, and occur in southern Africa. Small but numerous saline lakes are scattered through the western Rift Valley, especially in Uganda, and stretch northeast from Lake Chad. Soda lakes can be devided into two morphometric groups: broad, shallow pans and small, deep depressions. The broad, shallow pans usually stratify and mix each day, with calm stratified mornings followed by wind-mixing afternoons. Many of the small, deep lakes are chemically stratified and meromictic, but mix daily to the chemocline. Suspended mineral particles or dense phytoplankton are typical of these soda lakes, and vertical decrease of light is often very high. The Secchidisk commonly disappears within 30 cm (1% light at 6 cm depth, in Ngorongoro crater, Tanzania) Soda lakes are systems of extremes. Intervals of near-dryness alternate with periods of flooding and high water while salinity ranges through orders of magnitude in these lakes (e.g. Nakuru, Elementeita,….). The biota of soda lakes is depauperate. Nearly unispecific algal blooms can persist for years, and photosynthetic rates approach the highest measurements for natural communities. The soda lakes of tropical Africa are recognized as among the world’s most productive ecosystems. Persistent populations of the cyanophycean Spirulina platensis are commonly dominant supporting huge flocks of lesser flamingos (> 2 million); these are also used for human food. In these systems, we find typical species of algae, hemiptera, chironomid Diptera, anostraca etc. Solid salt deposits are a conspicuous feature of the margins of many shallow soda lakes. Some periodic removal by wind may occur. The relatively insoluble carbonates are particularly common, notable trona (Na2CO3.NaHCO3.2H2O), and less frequent a tufa of calcium and magnesium carbonates. Sodiumchloride occurs occasionally, e.g. in Lake Katwe (western Uganda). 5 Marelac Ugent – Lacustrine Systems April 2005 H. Eggermont Nakuru, Elementeita and Magadi, three broad shallow soda lakes lying in the Gregory Rift Valley of central Kenya, may be used to illustrate the biogeochemical dynamics of African alkaline saline lakes. The three lakes lie in semi-arid basins of internal drainage, and their levels and salinities fluctuate drastically in response to changes in rainfall and evaporation (dilution and evaporative concentrations) Generation of sediments Main sources are: (1) Allochtonous transfer of particles; (2) Chemical precipication; (3) Biological deposition. Hydrology Ratio of ponded water to river flow through it. At one extreme end you have systems whose flushing time is short. At the other extreme are closed lakes, or ones so nearly closed as Tanganyika [at modern rate flow the effluent Lukuga would take 5000 to 6000 years to discharge the volume of water equal that that which in ponded in the lake]: Seasonal changes in hydrology are particularly great in floodplain lakes of seasonally variable rivers; some completely evaporate to dryness. With it are associated species that have adapted their life histories in spectacular fashions (e.g., airbreathing lungfish, diapausing eggs, burrowing to a depth of 3 m into the dry sandy beds, …) Closed lakes (=no surface outflow) are commonly less seasonal partly because they are sustained by a groundwater reservoir that fluctuates less than rivers. Changes occur more slowly as a results of runs of relatively wet or dry years. For many lakes, including Victoria and Tanganyika, the main water losses are direct evaporation from the water surface. Hence, the lake balance is determined by evaporation-precipitation lake balance. [e.g., wet 1960s caused Tanganyika’s and Victoria’s lake water to rise several meters] Stratification and Mixing General notes: Stability (S) per unit area of a lake is the quantity of work or mechanical energy required to mix the entire volume of water to uniform temperature without addition or substraction of heat. The stability of a lake is strongly influenced by its size and morphometry. 6 Marelac Ugent – Lacustrine Systems April 2005 H. Eggermont Density differences are known to regulate stratification in lakes. The density difference between water at a given temperature and 1°C lower (= density difference per degree lowering) increase markedly at temperatures above and below 4°C. The amount of energy to mix water of different densities increases proportionally to the density differences. E.g., the amount of energy to mix layered water masses between 29° and 30°C is 40x, and between 24° and 25°C is 30x that required for the same masses between 4° and 5°C. In temperate lakes, the main determinant of the circulation are seasonal fluctuations of radiation and atmospheric temperature. The annual cycle of stratification in temperate lakes is dominated by the great difference in radiant heat income between summer and winter. Density stratification has its constraints on vertical distribution and aspects of photobiology that include O2/CO2 exchange, pH etc. Tropics, general features: We stated that the density difference per degree lowering is increasing markedly above 4°C so that the amount of energy to mix layered water masses between 29° and 30°C is 40x that required for the same masses between 4° and 5°C. This means in tropical lakes a relatively small difference in temperature between surface and deep waters may provide considerable thermal stability. What about seasonal fluctuations of radiation and atmospheric temperature in the tropics? Within the extensive range of latitudes (37°N-35°S) occupied by the African landmass, lakes are found under varied annual climatic cycles. Seasonal variation in radiation and hence temperature changes systematically with latitude, both as regard the amplitude (minimal near the equator) and phase. Within the tropical belt, latitudes <23°, the amplitude of seasonal variation of solar radiation and temperature are minimal. As northern starting point: a maroccan mountain lake at 2050 m elevation: an annual cycle similar to the northern temperate zone with low (= 5°C) winter temperatures and summer stratification, established by warming after March and ended by cooling and mixing in November-December. But when proceeding southwards, there are some important differences with the temperate zone: here, the major determinant of the circulation, and hence production, is wind-driven evaporative cooling (enhanced by low atmospheric humidity) rather than seasonal fluctuations of radiation and atmospheric temperature, although the influx of cool rains and reduced insolation during wet seasons can also be significant over a large part of Africa. Wind regime 7 Marelac Ugent – Lacustrine Systems April 2005 H. Eggermont and other components of the energy budget (like atmospheric turbidity/clouds) mostly display seasonal variation bearing no relationship to solar energy income. The best site example is Lake Pawlo among the Bishoftu crater lakes in Ethiopia: here a seasonal phase of cooling, typically in October-December, takes place not in the season of low solar radiation, but under combination of relatively high solar radation and low humidity. For other lakes, e.g. Victoria (0-2°), mixing is happening during the main incidence of the SE Trade winds in June-July. Other examples include mixing in Lake Opi (Nigerian savannah) during the annual impact of the dry harmattan wind. For this combination estimates of evaporative heat loss were high. In conclusion, at higher latitudes the ultimate and general controlling mechanism is undoubtedly the variable input of solar radiation, but near the equator seasonal differentiation is muted and hence other factors like wind regime, atmospheric humidity and turbidity, are more important. Overall, the tropics tend to be less windy than the temperate zones, but in many areas of subsaharan Africa are so windy that the work of the wind in disrupting stratification is quite high. Note that in tropical lakes, the anoxic lower layer is not always the equivalent of the hypolimnion. Tropics, various types of lakes and mixing regime (interplay between morphometry and factors of the energy budget): (1) Shallow lakes at low to mid-elevation (< 5m depth; <3000 m altitude): warm polymictic (frequent periods of circulation at temperatures well above 4°C). There are various case studies on such lakes, e.g. Lake George (area 250 km², mean depth 2.4 m). These lakes can undergo three types of cyclic environmental change: (a) a diel (24h) cycle of heat storage, stratification and mixing. The diurnal thermocline that quickly develops in the late morning and afternoon (cf. density stratification at >12-14°C!) affects phytoplanktonic sinking and accumulation or depletion of dissolved gases and mineral nutrients, much as do the seasonal thermoclines of the temperate zones. The daily stratification is ended by increased vertical mixing due mainly to a combination of reduced radiation input, increased wind strenght late in the day, and transfer of sensible heat to a cooler nocturnal atmosphere. Depending on the region in Africa, winds may or may not have a pronounced seasonality (e.g. July impact of the S.E. trades influential is part of East and central Africa). During the night, there is enhanced cooling and finally mixing. Exceptions include lakes with very good wind shelter!; (b) an annual cycle. This can have radically different forms depending on whether it is or not accompanied by entensive volume change during a flood-drying cycle (well-developed in many African floodplains). In a shallow basin of gently shelving morphometry, large changes of water volume due to hydrological factors lead to corresponding large horizontal excursions of water level as well as changes in mean depth. E.g. in the river-fed Lake Nakuru, there are radial extensions and contractions; Lake 8 Marelac Ugent – Lacustrine Systems April 2005 H. Eggermont Chilwa is more complex with asymmetric river inflow and shallows plus swamp which lead to freshwater rings; Lake Chad is even more complex as it consists of 2 basins, the deeper at greater distance from the main inflow. This fact and the development at low level of aquatic vegetation as obstacle to flow between basins, led to isolation of the deeper basin during low levels of 1973 and final drying out afterwards; (c) cycles of longer period, resulting from the succession of several dry or wet year (climate variation at time-scale of decades or longer, see Part II: Paleolimnology). (2) Lakes of intermediate depth, at low to mid-elevation (<100 m, <3800 m altitude): oligomictic, one to several mixing periods at irregular intervals throughout the year by occasional cooling of the surface.). For example, in Lake Victoria and Kariba, mixing is an annual event, sometimes accompanied by spread of anoxic water and massive fish kills. Lake Victoria has an enourmous surface area but is relatively shallow (max depth of 79 m; average depth of 40 m). From September to January there is a trend leading ultimately to stratification with a thermocline at 40 to 60 m between January and May (no more than 2°C difference between surface and bottom!). Breakdown of stratification happens during May to July: this is a period of the heavy southeast trade winds, resulting in increased evaporation and there may also be greater loss of heat by radiation at night. The onset of the calmer weather in August inaugurates another period of progressively increasing stratificiation. (3) The deeper lakes, at low to mid-elevation (>100 m, < 3800 m altitude): meromictic, staying stratified yearround (strata: monimolimnion, chemocline, mixolimnion). Especially tectonic and volcanic ones that are very deep relative to their linear extent ànd often windsheltered by crater rims or surrounding highlands, stratification may persist for many years. Above the level of permanent stratification, or chemocline, there may be a seasonal thermocline subject to annual or more frequent breakdown by evaporative cooling of surface waters during the windy season. Examples include Lakes Tanganyika and Malawi. Both lie in deep rifts orientated north-south, up which the powerful southeast trade winds are funnelled during the period from April to September. The seasonal alteration between this period of strong unidirectional winds with low rainfall, and the remainder of the year with variable and generally less violent winds and more rain, is the dominant influence on the hydrological regime. The power, direction, duration of the wind; the orientation of the lake and the surrounding topography all favour this condition. Partial mixing results in recycling of nutrients crucial for maintaining lake productivity (cf. endless summer of high surface T yearround accelerates all biological processes). Internal loading processes dominate nutrient cycling in deep tropical lakes. This includes erosion of the upper part of the anoxic layer by turbulence at the interface and 9 Marelac Ugent – Lacustrine Systems April 2005 H. Eggermont through movements in the anoxic layer itself associated with internal waves. Chemical and biological consequences of mixing: distribution of oxygen, transport of nutrients from depth to illuminated surface where phytoplankton can grow. Note that in some lakes, thermal stratification is frequently increased by a salinity difference between deep and surface waters, e.g. seasonally freshwater cap in closed lakes above residuum of more saline water built up by evaporation. Some pecularities: Some of these meromictic lakes display a strong temperature inversion (e.g., maar lake Mahega in western Uganda, has a Tmax of 40°C with cooler water above and below; a bloom of bacteria and blue-green algae at 1m depth absorbing solar energy to produce a warm layer). In other lakes like Lake Kivu, which is strongly stratified (~2000 years) by dissolved salts that are believed to come from sublacustrine saline springs, you have an accumulation gases (methane and carbon dioxide) to concentrations that exceed saturation at surface pressure! You can pump the gases up… In such heavily stratified lake upwelling of deep water rich in toxic gases (or very low in oxygen!) may cause widespread fish kills at the time (season) of circulation. Although no kill sufficiently extensive to destroy the fish fauna has been observed in modern times, probably such catastrophes are the reason why the fish fauan of this lake is much pooreer than that of its neighbors. Other examples include customary annual overturn in August 1976 in Lake Bosumtwi (Ghana) resulting in heavy mortality of cichlid fishes, and the 1984-1986 gas disasters of Lake Nyos and Monoun in Cameroon (killing >1700 people and life stock) (4) Tropical high mountain lakes (>3800-4000 m) = cold polymictic lakes, with frequent circulations during both day and nightstand of T below 12°C (normally slightly below or near 4°C). Glacial lakes present an interesting combination of equatorial insolation and very low temperatures. They lack any stable stratification (e.g., lakes at the foot of glaciers >5000 m on Mount Kenya are permanently below 4°C from top to bottom) because of relatively slight differences in the density of water within that thermal range. Two main items differentiate them from cold monomictic lakes (= lakes with frequent circulations in summer at low temperatures, typically even below 4°C): cold polymictic lakes enjoy throughout the year more or less constant light conditions at least with regards to the daily length of insolation (and more or less permanent fog keeps insolation on an equal level) and they mostly lack permanent ice covers (sometimes they do throughout the year or consecutive years by fluctuations of the snowline = amictic). Great number of cold polymictic lakes are found in the Andes (here we find several thousands, including the world’s biggest tropicial mountain Lake Titicaca and lakes located above 6000 m altitude), sub-tropical Himalaya (>6000 m), and ~100 lakes are known to occur in the East African mountains and Ethiopian mountains. Such lakes display even distribution of oxygen because of frequent mixing; those above the 10 Marelac Ugent – Lacustrine Systems April 2005 H. Eggermont vegetation belt often have no noteworthy amount of organic material and the chemical properties of lake water distinctly reflect the petrography of the catchment area. On Mt Kenya, they are embedded in maily pure alkaline rocks extremely poor in Mg; conductivity is almost pure a function of sodium concentration and neither Ca or Mg increases with growing conductivities. Concerning mixing regime in tropical high mountain lakes, even a lake like Titicaca, 16°S, 3800 m and max. depth 280 m has frequent circulation! If it would occur at lower altitude, such lake would be permanently stratified. Nutrient fluxes (these are in fact not so well-studied in Africa) Main fluxes are from: (1) River inputs: salt transportation by tropical rivers (2) Rain inputs: high inputs of total nitrogen from rain (fine terrigenous dust and photochemical reactions) may be common in Africa (3) Swamp inputs: many lakes are fringed by extensive and highly productive swamps (Cyperus papyrus, sedges, grasses…; living and dead stems, roots, decomposing peat). Such swamps can lead to nitrogen fixation and phosphorus absorption, though nutrient flux from such swamps is likely to be very large but not so well understood. Many of these (paryrus) swamps are more similar to a large septictank than to a filter: large amounts of debris are produced and settle to form a sludge, which provides nitrogen and enriched detritus for the often productive biota in the neighbouring waters. (4) Zooplankton: regeneration of nutrient; zooplankton excretion (5) Phytoplankton: mineralisation of dissolved organics excreted by phytoplankton or eroded off the sheaths of colonial blue-green algae; direct release of ammonia by phytoplankton. (6) other (and higher) levels of the food chain, zoobenthos, fishes, piscivorous fishes, crocodiles, birds - like flamingoes (feed on Spirulina) in the shallow soda lakes (e.g. Nakuru), can consume as much as 93% of the primary production (7) Hippo excretion (very common in the Kazinga channel, Uganda) (8) Export of fish (9) Sediments: release or uptake In temperate lakes, nutrient cycles are dominated by the physical processes governed by the thermal regime and light limitation. More specifically, outburst of productivity is triggered by rising temperature and illumination in spring, when surface waters are enriched by 11 Marelac Ugent – Lacustrine Systems April 2005 H. Eggermont nutrients during winter mixing. In the tropics, on the other hand, there is ‘endless summer’ (i.e., termperature and illumination are adequate yearround), and therefore biological control dominates the cycles of essential elements in lakes all year, rather than a few monts of the summer. Hence, production will be maximum for the available resources, and is stimulated by the onset of seasonal heavy winds which bring to the surface nutrients, which had been depleted above and had accumulated below during stratification. Smaller lakes seem to be more more P-limited and larger lakes seems to be more N-limited; annual productivity seems to be unaffected by like size. Large deep lakes are as productive as small shallow lakes. So, African lakes appear to violate the ‘first law of limnology’ (Fee 1979) stating that shallow lakes are more productive than deep lakes. However, meromictic lakes are evidently less productive than they would otherwise be if they were periodically completely overturned. The stagnant bottom layer is continuously accumulating nutrients derived from organic decompostion, of which only a portion is brought to the surface and reenters the production cycle. Of the major nutrient, Si is typically present – by world standards – in considerable concentration but liable to depletion by diatom growth; forms of N (nitrate) are typically present in low concentration (except for eutrophic systems) with some influence from denitrification; and P is often in considerable concentration, especially in many but not all soda lakes. Turbidity Can be considerable in shallow lakes (<5 m depth) where it is associated with particulate content, heavy development of phytoplankton, or from suspension of sediments and plant detritus (by wind, or influshing during the rainy season). Turbidity, or its reverse transparancy, can be measured by the depth of visibility of a Secchi disc. Lake Tanganyika: general limnology and some biological aspects General features: - Mean depth: 570 m; max depth 1470 m, deepest lake in East Africa (3rd on global scale); largest by volume in East Africa 12 Marelac Ugent – Lacustrine Systems April 2005 H. Eggermont - 75% of its volume is anoxic; the upper 200 m of oxygenated waters support a spectacular lacustrine biota (no measurable oxygen below 100 m in the north and 200 m in the south) - seasonal thermocline between 25 and 75m depth; and a permanent chemocline at greater depth - deep waters rich in phosphorus, silica and menthane (but not as much as in Kivu) - inflows relatively small, the Ruzzizi river being the largest (carrying so much dissolved material that its water dominates the chemistry of Tanganyika), coming from Lake Kivu. Also important is the Malagarasi from the east. Of the water loss, 90% is by evaporation from the free surface, only 10% goes out (water flowing westwards to the ocean through the Lukuga and Zaïre) - Nearly no nutrient input by rivers. Euphotic zone is nourished by regeneration of nutrient internally (recycling in the surface waters) and from the depths (through the thermocline and chemocline; and localized seasonal upwelling of deep water near the south end, especially from July to September and from November to December, when strong southerly winds blows up the lake. This upwelling, also featured in the similarly shaped and oriented Malawi, is associated with a phytoplankton pulse). - >1500 m of sediments, with sedimentation differing widely in different parts of the lake (in rate and nature!) - very transparant, with a Secchi disc visibility of as much as 20 m; low rate of nutrient loading from effluents = misconception that Tanganyika is an oligotrophic unproductive lake (thousands of tons of fish each year) - lake level changes during its history have been considerable. During pleistocene, when African lake levels were generally low, the level dropped several hundred of metres. Endemism In Tanganyika, you find lots of endemic species and genera, especially in the fish fauna (173 out of 193 species are endemic; 40 genera are endemic vs Kivu only 17-18 species present of which 7 or 8 are endemic); there are also many endemic ostracods, copepods and molluscs, and even 2 endemic snakes. Although ancient lakes in other parts of the world contain species that are endemic to them, and Lake Baikal on top, no other lake district presents so many examples of radiative speciation from a limited number of parent stocks. Malawi, Victoria and Tanganyika contain >100 endemic fishes (98% of the cichlid fishes; 57% of the non-cichlid fishes are endemic). What is the reason for high endemism?: There are various hypotheses. It is conventionally believed that speciation requires the geographic separation of 2 populations which then diverge sufficiently to prevent inbreeding. Lakes Malawi and Tanganyika have 13 Marelac Ugent – Lacustrine Systems April 2005 H. Eggermont long shorelines consisting of alternating stretches of sandy beach and rocky cliff. It is postulated that each of these two types of habitats acts as a series of islands, and that the intervening stretches of the other habitat provide effective isolation; gene flow between the islands is reduced to such an extent that evolutionary divergence can proceed to the level of reproductive isolation. Lake-level changes that are known to have occurred in tropical African lakes over a time-scale of tens of thousands of years would be sufficient to merge or partition sandy beaches and rocky headlands, so populations could be split and reunited from time to time. If reproductive isolation had been established by the time of reunion, and if competitive interaction between the daughter species did not provide an insuperable advantage to either of them, one would have two species where only one had been before. Lake Victoria has a much more elaborate shoreline, less easily categorized into separate habitats, but it swarms with islands that could provide the required geographic separation, and you also have beach ponds where isolation can occur. It has also been suggested that the lakes were separated into distinct basins during the course of their history. Tanganyika does, in fact, contain several distinct basins, and a fall in water level of 750m would separate it into three lakes; a fall of 1250m would create four. Lake Victoria may have consisted at an earlier stage in its history, of a number of separate small lakes (separate basins created by tectonic activity, but now united with the main lake). Although water level change would not separate it into separate large lakes like Tanganika, there are several small closed basins which could have been the home of isolated, differentiating aquatic populations whenever the main lake dried up completely. All these hypotheses are reasonable, although it must be recognized that they rest more on hypothesis than evidence. They provide no explanation for the presence in Barombi Mbo, a small volcanic crater in Cameroon with a simple bowl-shaped basin and uniform shore of 12 endemic species of fish. A number of other groups on animals, all of them associated with the bottom rather than open water for at least some critical part of their lives, have developed species flocks. The gastropod molluscs of Tanganyika have attracted the most attention, in part because some of them have thick or elaborate shells reminiscent of marine species. After a long debate of a hypothetical former connection between Tanganyika and the sea, it is now clear that these gastropods are of fresh-water origin. The heavy or ornamented shells characteristic for some of the opistobranch gastropods are adaptions to the high wave energy of this enormous lake, even if though many of the ornamented gastropods live well below the surge level. It might also be an adaptive advantage in coping with specialized mollusc predators such as shell-crushing cichlids. 14 Marelac Ugent – Lacustrine Systems April 2005 H. Eggermont Human impact Concerning human impact, it is noteworthy that tropical lakes may not function in exactly the same way as temperate lakes. Impacts to which these lakes are exposed include: - eutrophication (resulting in persistent anoxia, fish kills, impact on nutrient recycling…) - soil erosion and increased sedimentation as a result of enhanced deforestation in the catchment - species introduction, e.g. Nile Perch (’50) and Tilapia (’60) for commercial fish catch (up to 200 kg!) in Victoria let to enormous decrease in number of endemic species and population size - overfishing - … Selected references on African Limnology: Batterbee, R.W., Gasse, F., Stickley, C. (Eds.), 2004. Past climate variability through Europe and Africa. Springer, Dordrecht, The Netherlands, 637 pp. Beadle, L.C., 1974. The inland waters of Tropical Africa – An introduction to tropical limnology. Longman, London, 365 pp. Johnson, T.C., Odada, E.O. (Eds.), 1996. The limnology, climatology and paleoclimatology of the East African lakes. Gordon and Breach Publishers, Toronto, Canada, 664 pp. Kilham, P., 1990. Mechanisms controlling the chemical composition of lakes and rivers: data from Africa. Limnol. Oceangr. 35(1): 80-83. Livingstone, D.A., Melack, J.M. , 1984. Some lakes of subsaharan Africa. In: F.B. Taub (Ed.) Lakes and reservoirs, Elsevier Science Publishers, Amsterdam, The Netherlands. Löffler, H., 1964. The limnology of tropical high-mountain lakes. Verh. Int. Ver. Limnol. 15: 176-793. Löffler, H., 1968. Tropical high mountain lakes. Their distribution, ecology and zoogeographical importance. Colloquium Geographicum Band 9. Talling, J.F., 1969. The incidence of vertical mixing, and some biological and chemical consequences, in tropical African lakes. Verh. Internat. Verein. Limnol. 17: 998-1012. Talling, J.F., 1992. Environmental regulation in African shallow lakes and wetlands. Rev. hydrobiol. Trop. 25(2): 87-144. Talling, J.F., Lemoalle, J. (Eds.), 1998. Ecological dynamics of tropical inland waters. Cambridge University Press, UK, 452 pp. Talling, J.F., Talling, I.B., 1965. The chemical composition of African lake waters. Int. Revue ges. Hydrobiol. 50(3): 421-463. Wetzel, R.G. (Ed.), 1983. Limnology. Second edition, Saunders College Publishing, US, 767 pp. 15 Marelac Ugent – Lacustrine Systems April 2005 H. Eggermont Part II Paleolimnology II.1. Paleoclimatology Paleoclimate research in Africa is an international research priority coordinated by the programmes Past Global Chages (or PAGES) and International Decade of East African Lakes (or IDEAL). ?Why doing paleoclimate research Knowledge of past climate variability (at decade-to-century time scales) is the foundation for understanding and modelling current and future climatic trends. Long-term perspective of natural climate variability is needed to be able to discover underlying mechanisms of climate variation and to evaluate the impact of humans on future climate. People are now building a global network of accurate and high-resolution climate reconstructions, with special attention going to the tropics because this region is the heat engine of the global climate system, and it is also the region from which we lack a lot of paleoclimate data. ?Why focusing on East Africa? Throughout tropical Africa, and dryland regions of East Africa in particular, knowledge of drought frequency and intensity is crucially important for the development of good landscape and water-resource management practices in agriculture, freshwater fisheries and hydroelectric power generation. ?How to obtain long-term perspective of climate variability in East Africa? In East Africa, instrumental weather and documentary records from before the colonial period are very rare and too short; therefore these records do not offer a lot of information. There is also limited potential of natural archives traditionally used to reconstruct climate in northern temperate regions such as tree rings [very few African trees develop distinct annual growth rings because of muted seasonality, and those that do rarely grow older than 100 years; also dead logs and construction timber is rarely preserved long enough to be of any use in extending the historical record], ice cores [very few snow-capped East African mountains; on Ruwenzori and Mt Kenya climate signals are corrupted by intermittent meltwater percolation; the only potential lies in the ice field on Mt Kilimanjaro], speleothems and corals [both limited in geographical distribution, with speleothems only in extra-tropical north and south Africa; corals in the Indian ocean coast]. Hence, lake sediments that accumulate on the bottom of climate-sensitive lakes are the principal source of information on the climate history of tropical East Africa. ‘Climate-sensitive’ lakes are lakes that 16 Marelac Ugent – Lacustrine Systems April 2005 H. Eggermont (1) that clearly respond to short-term climate change (=sensitivity) (that clearly display lake-level fluctuations through time) AND (2) that have a continuous sediment record (= longivety) (that have survived the most arid periods without dessication or erosion of sediments) These two criteria should certainly be met. In East Africa, it is certainly a huge challenge to find lakes showing good balance between longivety and hydrological sensitivity. In the sediment of these lakes, several paleoclimate indicators can be found, not only biological proxies (species composition of subfossil algae, invertebrates, pollen) but also non-biological proxies (sediment composition, geochemical signals). Every proxy can tell something about past climate, every proxy has its strenghts and weaknesses so to get a more reliable and integrated picture of climate change, one needs to compare reconstructions based on several independent proxies (= multi-proxy studies) The best-resolved multi-proxy reconstruction of rainfall and drought yet available from equatorial east Africa is based on a sediment record recovered from Lake Naivasha, Kenya (Verschuren et al. 2000). This record covers last 1800 years (~8 m of sediment core), it has a decade-scale resolution and excellent age control because all factors confounding chronology were carefully studied. Ppt-slide 94: illustrated are lake-level fluctuations over the past 2000 years inferred from sediment stratigraphy, and salinity fluctuation inferred from species composition of fossil diatom and fossil midges (chironomids). High salinities correspond with low lake; low salinities correspond to high lake level, hence there is generally good agreement between reconstruction based on the different proxies. These data show that the climate of central Kenya over the past 2000 years has been characterised by a succession of (at least) 7 (decade-scale) dry periods more severe than any drought recorded during the 20th century. These periods are indicated in yellow [and called Naivasha drought 1 to 7]. Ppt-slide 95: Illustrated is the lake Naivasha lake level reconstruction with focus on the past 1100 years. During the MWP (Medieval Warm Period; ~1000-1270 AD, when there was medieval warming in north-temperate regions) climate was significantly drier than today and that during the LIA (Little Ice Age; ~1270-1850, when Europa enjoyed great cooling) climate was relatively wet, with a significant highstand between 1670-1770. However, the LIA was also interrupted by three episodes of severe aridity; especially the dry period at ~200 years was tremendous and a lot of inland waters completely dessicated. From this, it clearly shows that tropical climates have been anything but stable during the Holocene unlike previously stated. Further illustrated is the pre-colonial history of East Africa recounted in oral traditions and historical sources: the dry periods are associated with periods of famine, 17 Marelac Ugent – Lacustrine Systems April 2005 H. Eggermont political unrest and large-scale migration, while the wetter periods concide with periodes of prosperity. This clearly shows the importance of rainfall and drought in agricultural and pastoral societies, and the strong link between cultural development and climate change. Altogether, this study certainly underlines the importance of lake-based paleoclimatology. Of course, one core is not enough to represent climate history throughout equatorial Africa. Climate records from the large African Rift Lakes Tanganyika and Turkana lack comparable detail and age control, but are consistent with our inference that tropical East Africa was drier during 11th and 12th centuries and relatively wet from the late 13th to mid 18th century. The extreme drought at ~ 200 years ago is also visible from these records, and similar patterns also occur in several (typically incomplete) records from shallow fluctuating lakes in the region, e.g. from Lake Chilwa in Malawi and Lake Chad in the Sahel. When looking at data coming from southeast tropical Africa, dry Medieval period and maximum aridity at ~200 years ago is also visible (which means these are continental scale events) while trends during most of the LIA period were opposite (increasing or decreasing moisture trends). In fact, this apparent alternation between episodes of interregional contrasts in climate and episodes characterised by continent-wide events is not unexpected as it simply reflect varying influence of distinct climate-forcing mechanisms working at different timescales. One core is also not enough to elucidate all external and internal climate-forcing mechanisms. As for external forcing, it seems that dry Naivasha periodes broadly coincide with phases of high solar radiation, and intervening wet periods coincide with phases of low solar radiation. Especially, highest inferred rainfall of the past 1100 years is coeval with the Maunder minimum in solar radiation (~AD 1645-1715). Hence, solar forcing may have contributed to decadal-scale rainfall variability in equatorial East Africa. As for internal forcing, there is indication of influence of Indian monsoon variability but also processes in the Atlantic ocean seem to be (at least partly) responsible for climate-variability at decade-tocentury time scales. One core is not enough to evaluate links between climate variability in Northern hemisphere and tropical regions and to produce realistic forecasts of future climate change under changed boundary conditions of human-induced climate change. Temperature rise during the past 2 decades is already outside the range of natural climate variability. Hence, human impact is certainly an important player to take into account. It is clear that it is quite a job to answer all these questions. Ongoing research is now exploring the full potential of African lake sediments as recorders of past climate variability. Over the past 4-5 years, some 75 permanent standing waters throughout equatorial East 18 Marelac Ugent – Lacustrine Systems April 2005 H. Eggermont Africa were studied. Some 60 lakes are located in Uganda and Kenya. Study sites in Uganda are mostly crater lakes located in four maar-crater districts in Western Uganda. Crater lakes are preferred sites for climate reconstruction because many of them display reasonably good balance between longivity and hydrological sensitivity. Study sites in Kenya include all the main tectonic lakes and associated crater lakes in the dry Eastern Rift valley, freshwater lakes on its moist shoulders to the east and west, the Nyanza Gulf of Lake Victoria, and shallow lakes and swamps in Amboseli and Nairobi National Parks. All these Ugandan and Kenyan lakes constitute a very diverse data set with lakes covering a broad salinity gradient as they range from very dilute up to lakes 4x as salt as seawater (100-135,400 S S/cm); they also display diverse combinations of lake area, depth, mixing regime and catchment disturbance. As such, they represent the full regional diversity of climate-driven environmental conditions, and can be considered a unique natural laboratory for doing paleoclimate studies and for calibrating climate indicators. Field data are of all kind. To evaluate longivity and hydrological sensitivity, lake morphometry was mapped using echosounding, elevation points were taken along the craterrim; notes on catchment characteristics were taken often in combination areal photographs and recent satellite images. In addition, water samples were collected as well as profiles of oxygen, pH, salinity and T etc. Based on all these data, and on rough evaluation of local sedimentation conditions and hydrological sensitivity, some 27 sites have now been selected as potential sites for high-resolution climate reconstruction. From these lakes, short sediment cores were taken spanning ~100-250 years. More detailed sedimentological analysis, preliminary sediment dating and rapid biological screening was necessary to evaluate the real potential of these site for high-resolution climate reconstruction. Ppt slide 109: illustrated are the results of sediment analyses from 3 short cores (2 from Uganda – 1 from Kenya); in the sediment stratigraphy, there are clear signatures of the dry event 200 years ago. However, based on Pb and C14 dating it seems that none of these lakes display a continuous sediment archive; they likely dessicated during dry events – hence they do not constitute good sites for long-term climate reconstruction. In fact, only 10 of the investigated sites display good balance between sensitivity and longivety. From these sites, long sediment cores were recovered which now form the basis for a network of climate reconstructions across tropical East Africa over at least the past 2000 year. Lake Wandakara (ppt slide 111) in Western Uganda is such a lake, with clear climate signals in the sediment record and continuous sedimentation. One of the most promising sites we discovered for climate reconstruction is Lake Challa (ppt slide 112-113), a deep (97 m) permanently stratified crater lake on the lower East slope of Mount Kilimanjaro (southeastern Kenya). Seismic-reflection profiling in January 2003 yielded a detailed bathymetry and revealed very uniform sediment deposition across the central lake bottom. 19 Marelac Ugent – Lacustrine Systems April 2005 H. Eggermont Exploratory Pb and C-dating of short cores indicate an average Holocene sedimentation rate of ~1m per 1000 years, which means that the last 21,000 years are covered by the upper 18 to 20 meters (Late glacial + complete Holocene). The short cores are very finely laminated over their entire length holding clear signals of climate change As stated before, the current East African data set is – in many ways - very diverse; hence it also constitutes the perfect basis for calibrating climate indicators, which means that we analysed their variation in surface sediments of lakes spanning the full modern gradient of climatically controlled environmental factors. From all lakes, surficial lake sediments were collected with recently deposited death assemblages (of diatoms, crustaceans, aquatic insects, …). Analysis of these subfossil remains provides information on modern species distribution, information which is extremely valuable when making either qualitative or quantitative interpretations from long sediment cores. ?Avenues for future research (1) Multi-proxy study of the long sediment records to obtain regional network of climate reconstructions. Especially the continuous and finely laminated sediment record of lake Challa (low East slope of Mt. Kilimanjaro) is a very promising site to reconstruct – with excellent time resolution and age control – the complete post-Glacial history of climate variation in equatorial East Africa. (2) Preliminary analysis of chironomid remains on Mt Kenya and the Ruwenzori Mountains (Uganda – DR Congo) show clear potential for development of African chironomids as quantitative indicators for temperature (a paleothermometer) independent of moisturebalance change. Selected references on African paleolimnology Verschuren D., Laird K.R. & Cumming B.F, 2000. Rainfall and drought in equatorial East Africa during the past 1100 years. Nature 403: 410-414. Verschuren D., 2004. Decadal and century-scale climate variability in tropical Africa during the past 2000 years. In Batterbee R.W. et al. (Eds.). Past climate variability through Europe and Africa. Kluwer Academic Publishers, Dordrecht, The Netherlands. II.2. Human impact studies Paleolimnological techniques can also be used to reconstruct the environmental changes to which lakes and adjacent landscape are exposed. Case study: 20 Marelac Ugent – Lacustrine Systems April 2005 H. Eggermont Verschuren D., Johnson T.C., Kling H.J., Edgington D.N., Leavitt P.R., Brown E.T., Talbot M.R. & Hecky R., 2001. History and timing of human impact on Lake Victoria, East Africa. Proc. R. Soc. Lond. B. 269: 289-294. 21