The palaeo-environmental history of equatorial East Africa ... · East Africa: Implications from...
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FACULTY OF SCIENCES
Master of Science in geology
Academic year 2015–2016
Master’s dissertation submitted in partial fulfillment of the requirements for the degree of Master in Science in Geology
Promotor: Dr. I. Meyer
Jury: Prof. Dr. D. Verschuren, Prof. Dr. G. Weltje
The palaeo-environmental history of equatorial East Africa: Implications from mineralogy and
particle-size distributions
Niels Tanghe
Cover image. View on Lake Challa (Credit: www.tanzania-experience.com)
Acknowledgements
This thesis would have never been possible without the help and support from a lot of people, and
therefore I would like to seize the opportunity to thank them.
First, I would like to thank my promoter, Dr. Inka Meyer, for giving me the chance to work on this
very interesting topic. She was always available for help, whether it regarded discussion of my
results, correcting my text or some help in the lab when two hands were just not enough. Her help
and support guided me to the finish line, and I appreciate that very much. I would also like to wish
her a lot of success in her upcoming project(s).
I would also like to thank Ann-Eline Debeer, for her professional explanation of the heavy liquid
separation method and for her help with the SEM.
I much enjoyed working together with Jonas during the last few months, and therefore I would like to
thank him personally. I also very much appreciate him for letting me use his data in this thesis.
I would also like to dedicate some words to my classmates and friends. These last five years wouldn’t
have been the same without them, and therefore I would like to thank them for all the fun moments.
In particular, I would like to thank Thomas, Tycho and Loic for the great times during the last five
years.
Finally, I would like to thank my parents and sister for their endless support and love during the last
five years, and for allowing me to follow my own path.
Table of contents
CHAPTER I. Introduction and research objectives .................................................................................. 1
CHAPTER II. Study area ........................................................................................................................... 4
2.1. Geological setting .................................................................................................................... 4
2.2. Present day climatic setting .................................................................................................... 6
CHAPTER III. East African environmental variability .............................................................................. 8
3.1. Environmental evolution of equatorial East Africa since the LGM ......................................... 8
3.2. Lake Challa proxies ..................................................................................................................... 11
CHAPTER IV. Material and methods ..................................................................................................... 14
4.1. Grain-size analysis ...................................................................................................................... 14
4.2. End-member modelling analysis ................................................................................................ 17
CHAPTER V. Results .............................................................................................................................. 19
5.1. Grain-size analysis ...................................................................................................................... 19
5.2. End-member modelling .............................................................................................................. 21
5.2.1. End-member Analysis (EMA) ............................................................................................... 21
5.2.2. End-member variations ....................................................................................................... 24
CHAPTER VI. Discussion ........................................................................................................................ 29
6.1. Identification of the end members ............................................................................................ 29
6.1.1. End member 1 ..................................................................................................................... 30
6.1.2. End member 2 ..................................................................................................................... 30
6.1.3. End member 3 ..................................................................................................................... 32
6.1.4. End member 4 ..................................................................................................................... 33
6.1.5. End member 5 ..................................................................................................................... 35
6.2. Paleo-environmental implications of the dust fraction ............................................................. 36
CHAPTER VII. Conclusions ..................................................................................................................... 38
REFERENCE LIST ..................................................................................................................................... 40
APPENDIX .............................................................................................................................................. 44
Chapter I – Introduction and research objectives
1
CHAPTER I. Introduction and research objectives
Terrigenous particles from sedimentary records have proven to yield valuable information when
reconstructing paleoclimatic conditions and paleo-environments (Hamann et al., 2008; Holz et al.,
2007; Stuut et al., 2002). By definition terrigenous sediments derive from on-land sources and are
transported by different mechanisms to the side of deposition. Their initial formation is influenced by
the dominating weathering regime on land. Cold/arid conditions results typically in more physical
weathering of rocks, while warm/moist conditions are characterized by increased chemical
weathering. Rivers are the major mechanism for transportation of terrestrial sediments on a global
scale (Milliman and Syvitski, 1992). However, aeolian transport is also an important transportation
mechanism, especially in (semi-)arid environments. Wind-blown sediments can be transported over
very large distances depending on the wind speed and shear stress. For example, Saharan dust is
partly transported to the Bahamas (Ott et al., 1991) or to South America (Prospero et al., 1981).
Sediment transport through ice is the third mechanism and commonly results in a poorly sorted
debris comprising different grain-size classes. However, this process is restricted to areas where ice
masses are present. Figure 1.1 illustrates different mechanisms which lead to deposition of clastic
particles into a basin. Variations in physical properties, like sediment texture, particle shape and
variations in grain-size of terrigenous sediments were frequently used in order to gain information
about sediment transport mechanisms, depositional processes and sediment provenance (Krumbein,
1941; Passega, 1957; Visher, 1969). However, the information that can be extracted only from the
grain size of particles is limited, since the clastic particles in a basin are often a mixture from
sediments with different provenance and/or they are deposited by different transportation
mechanisms (Weltje and Prins, 2007; Weltje and von Eynatten, 2004). This mixture of signals is
expressed by a typical polymodal grain-size distribution of clastic samples (Holz et al., 2007).
Figure 1.1.: Sketch illustrating different mechanisms for transportation of clastic sediments to a basin. 1) transport of aeolian sediments. 2)
sediment transport by rivers. 3) transport of sediment by ice. 4) alluvial fan transport.
One way to overcome this problem is applying a complex statistical end-member model. This method
allows to identify distinct sub populations (end members) in the sediments based on their grain-size
distributions. Each identified end member is representing a sediment fraction which has the same
provenance and/or which was deposited by the same mechanisms. Unmixing of the terrigenous
fraction into end members helps understanding depositional processes and sediment provenance for
various environments (Paterson and Heslop, 2015; Weltje and Prins, 2003). In Africa, sediment
unmixing studies mostly concerned reconstructing wind and rainfall patterns using the aeolian
Chapter I – Introduction and research objectives
2
fraction in the sediments (Meyer et al., 2013; Stuut et al., 2002), although reconstructions of
sedimentation processes were also frequently performed (e.g. Holz et al., 2004).
This study aims to reconstruct paleo-environmental conditions in tropical East Africa using the clastic
sediment fraction from Lake Challa, a freshwater lake situated on the border between Tanzania and
Kenya. Sedimentary records in equatorial Africa hold important information on low-latitude climate
processes. Moreover, they provide answers to enduring questions on how external climate forcing
created climate changes in this area. For example, precessional-driven variations in summer
insolation at the Equator seems to have generated variations in monsoonal rainfall which were in
phase with the orbital forcing mechanisms (Verschuren et al., 2009). Lake Challa provides an ideal
study location to answer these questions. Due to its equatorial position (3.3° S), both Northern and
Southern Hemisphere climatic signals are recorded. The Intertropical Convergence Zone (ITCZ) passes
twice a year over the lake (fig 1.2 A), resulting in a bimodal rainfall pattern of two wet seasons and
two dry seasons (fig 1.2 B). This results in two monsoonal seasons, from a SE direction during
Northern Hemisphere summer and from NE direction during winter. The latitudinal range in the
migration of the ITCZ is maximal in East Africa, which enhances the monsoonal dynamics. Since Lake
Challa is always situated east of the Congo Air Boundary (CAB), the influence of Atlantic moisture in
the lake is minimal (Tierney et al., 2011b). High-latitude Northern Hemisphere climatic signals, which
were transported to lower latitudes by the Atlantic thermohaline circulation, do not reach the lake as
a consequence. Hence, Equatorial East Africa remained relatively unaffected to signatures of
Northern Hemisphere ice sheets.
Figure 1.2.: A) Position of the Intertropical Convergence Zone (ITCZ) and the Congo Air Boundary (CAB) in July (Northern Hemisphere
summer) and January (Southern Hemisphere summer). The location of Lake Challa is indicated with C. The red square indicates the area
that is shown in figure 2.3 (modified from Verschuren et al., 2009). B) Climatogram for Challa, Kenya (data from
www.worldweatheronline.com).
Extensive studies have been performed on Lake Challa and its sedimentary infill, mainly in framework
of the CHALLACEA research project (2005-2008). Reconstruction of the lake-level fluctuations
revealed that Lake Challa experienced some major episodes of desiccation, but never dried out
completely, providing therefore one of the few continuous paleo-records from equatorial East Africa
(Moernaut et al., 2010). These observations were acknowledged by reconstruction of the local
monsoon rainfall (Verschuren et al., 2009). Other studies mainly focused on the biogenic fraction
which is present in the lake, since this is the main component in the lake sediments (up to ~70 %)
Chapter I – Introduction and research objectives
3
(Barker et al., 2013, 2011; Kristen, 2010; Milne, 2007; Sinninghe Damsté et al., 2011). The
comprehensive study of Lake Challa confirms the excellent quality of the sedimentary record. Lake
Challa will be the subject of an ICDP drilling later this year, further underlining the importance of this
research.
The terrigenous fraction in the sediments from Lake Challa have never been studied however, mainly
because of the rather low abundance of detrital minerals in the sediments. The processes which led
to transportation and deposition of the different terrigenous particles to the lake are still unclear,
and therefore this study aims to solve the following questions.
(i) What are the different transportation mechanisms which led to the deposition of
terrigenous particles in Lake Challa?
(ii) Are we able to document variations of aeolian input versus run-off of clastic particles in
Lake Challa during the last 25 ka?
(iii) Can we link the obtained results with other relevant proxies in order to extract
information about climatic variations in equatorial East Africa?
In order to find answers to these research questions, high-resolution grain-size analysis on the
CHALLACEA composite core will be performed using laser diffractometry on 178 distinct samples.
Following, the obtained grain-size distributions will be unmixed into representative sub populations
using the end-member modeling software AnalySize (Paterson and Heslop, 2015). The identified end
members will represent sediment fractions which share the same provenance and transportation
mechanisms. With the findings obtained by this study we will be able to close an important gap
which is still existing in the Lake Challa record.
This dissertation is divided into multiple chapters. Chapter II regards the regional setting of Lake
Challa, as well as the present-day climate that is present in Equatorial East Africa. The environmental
evolution of East Africa since the Last Glacial Maximum is described in chapter III, since the
sedimentary record of this study spans this time frame. Chapter III further summarizes some
important studies that have already been performed on Lake Challa, in order to give a
comprehensive view on how this study fits into the broad framework that already has been
established on the lake. A detailed explanation of the used material and methods is given in chapter
IV. Results are given in chapter V, as well as a step-by-step walkthrough on how the end-member
modelling was applied in this study. A comparison of the obtained results with other proxies is given
in chapter VI. All identified end members are interpreted and discussed in terms of paleo-
environmental implications for the study area. Finally, a conclusion will be made and the used
literature will be referenced. The appendix can be found at the end of this thesis.
Chapter II – Study area
4
CHAPTER II. Study area
2.1. Geological setting
Lake Challa is a small freshwater lake filling a volcanic caldera on the lower east slope of Mt.
Kilimanjaro (3.3°S; 37.7°E), right on the border between Tanzania and Kenya (Fig 2.1). The lake has a
surface area of ~4.2 km² and is situated at 880 m altitude. Lake Challa has a water depth of
approximately 95 m, with fluctuations between 92 and 98 m during the period 1999-2008 (Moernaut
et al., 2010). The caldera has a Pleistocene age and is situated within the rocks of the Kilimanjaro
complex. This volcanic complex is mainly composed of trachy-basalts, resting on a metamorphic
basement rock predominantly consisting of gneisses (Petters, 1991). These gneisses outcrop south
and east of Lake Challa. On top of the trachy-basalts lies a calcite-cemented tuffaceous breccia which
formation is most likely related to the formation of the crater (Downie and Wilkinson, 1972). This
“calcareous tuffaceous grits” are found on the south-eastern crater walls, while the rest of the crater
rim is mostly build out of the trachy-basalts from the Kilimanjaro complex (Kristen, 2010).
Figure 2.1.: Satellite image of the study area and its surroundings. Lake Challa is situated on the lower east slope of Mt. Kilimanjaro. The
yellow dotted line indicates the border between Tanzania in the West and Kenya in the East. The yellow square indicates the area shown in
figure 2.2A. The inset shows the location of the study area within the African continent, indicated with a red square (Satellite image:
Google Earth).
The crater lake is filled with a sedimentary succession of ~210 m thickness, covering the last
~250,000 years (Moernaut et al., 2010). Lake Challa is not fed by any rivers and there are also no
rivers draining the lake. Hence the water balance of the lake is controlled by subsurface in- and
outflow, local rainfall of ~600 mm/yr and evaporation of ~1700 mm/yr. Subsurface inflow of water
originates from precipitation water percolating from the montane forests upslope of Mt. Kilimanjaro.
This percolated water reaches Lake Challa within approximately 3 months (Moernaut et al., 2010).
Based on the artificial injection of tritium isotopes, Payne (1970) estimated the subsurface in- and
outflow of Lake Challa to be 12.5 x 106 m³ and 8.2 x 106 m³, respectively.
Chapter II – Study area
5
Figure 2.2.: A) Satellite image of Lake Challa and bathymetrical map of the lake. Contour intervals are every 10 m, with a maximal depth of
94 m during time of acquisition. The white dotted line represents the crater catchment area. The yellow dotted line is the border between
Tanzania in the West and Kenya in the East. The red dot in the centre of the lake is the coring location of the CHALLACEA core used in this
study. The red line indicates the location of the 3D seismic profile shown in figure B, the red arrow shows the viewing direction on this
seismic profile (Satellite image: Google Earth; bathymetric map modified from Moernaut et al., 2010). B) 3D visualization of the
sedimentary infill of Lake Challa. The virtual surfaces were created by interpolation of seismic reflectors. The basement surface is
characterized by the presence of volcanic cones which separate the basin into three depressional areas, from which two are visible. The
green line indicates the projected location of the CHALLACEA core (modified from Moernaut et al., 2010).
Chapter II – Study area
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The lake is surrounded by steep crater walls, reaching a height of 170 m above the modern lake
surface at certain places. These walls also limit the lake catchment area (1.38 km²) (Buckles et al.,
2014). The catchment can only be enlarged in the northwestern corner of the crater, were a 300 m
long creek is present. However, a contribution from the creek most likely only occurred during
periods of very heavy rainfall (Kristen, 2010).
The water masses of Lake Challa are stratified during the two wet seasons which run from October to
December and from March to May, respectively, classifying Lake Challa as a meromictic lake. The
epilimnion is limited to the upper 20 m in the water column. During the dry and more windy season
between January to February and June to September, the epilimnion drops to depths of about 50-60
m (Kristen, 2010). These seasonal variations are also reflected in the sediments of Lake Challa. The
deep mixing of the water layers from June to September provides nutrients, which results in a diatom
bloom during these months. Detrital minerals are mainly deposited during wet seasons.
Moernaut et al. (2010) acquired a dense grid of high-resolution seismic profiles in Lake Challa during
a field campaign in 2003. Further, the bathymetry of the lake was acquired during this campaign (fig
2.2A). Lake Challa has a bowl-shaped bathymetry with a maximal water depth of 94 m at the time of
data acquisition. The upper slopes are dipping between 30° and 90°, while the sediments at the
center of the lake are slightly dipping (1 – 5°). The break in slope between the sediments on the outer
parts and the sediments on the inner parts of the lake is relatively sharp and is situated at 60 – 70 m
water depth. A 3D view (fig 2.2 B) across the lake was created by Moernaut et al. (2010) and shows
the presence of volcanic cones on the bottom of the lake, which initially separated the basin into
three depositional areas (depression 1-3). Two of the three depositional areas are visible in figure 2.2
B.
2.2. Present day climatic setting
Due to the tilt of Earth’s axis, solar insolation reaches a peak twice a year at the Equator, causing two
monsoonal systems. During the periods of maximal solar insolation, the African continent warms up,
resulting in a low pressure area above the continent. Moist air is brought in from the Indian Ocean,
resulting in monsoonal rains above the African continent. Shifting of the peak solar insolation also
results in migration of the Intertropical Convergence Zone (ITCZ) and the Congo Air Boundary (CAB),
northward during Northern Hemisphere’s summer and southward during Southern Hemisphere’s
summer (fig 1.2 A). The local climate at Lake Challa is tropical semi-arid with a bimodal rain
distribution (fig 1.2 B). From October to December the monsoon coming from a northeasterly
direction, providing “short rains” to East Africa (fig 2.3). From March to May, the monsoonal winds
are provided from a southeasterly direction (fig 2.3), providing “long rains” which are characterized
by more rainfall, although the total amount of rainfall is still relatively low (less than 300 mm during
the March – May season) due to the equatorial location (Camberlin and Okoola, 2003). Nicholson
(1996) described that the monsoonal winds in East Africa are rather dry. Dry NE monsoonal winds are
associated with its passing over the eastern Sahara and with cool waters in the Arabian Sea. The SE
monsoonal wind loses humidity along the East African coast due to friction with the shoreline. The
“short rains” in equatorial East Africa are positively correlated with the El Niño Southern oscillation
(ENSO) and with large-scale sea surface temperatures (SST) anomalies in the Indian Ocean (Black et
al., 2003; Mutai and Ward, 2000), while the “long rains” show little to no correlation with ENSO or
SST-anomalies (Camberlin and Philippon, 2002). Varve thickness variations from Lake Challa indicated
Chapter II – Study area
7
that El Niño years are characterized by increased rainfall, while La Niña years tend to be more dry
(Wolff et al., 2011).
The shifting position of the ITCZ and the CAB is shown in figure 1.2 A. The CAB is the convergence
zone of moisture brought from the Atlantic vs. Indian Ocean. Zonal patterns in the hydroclimate of
equatorial Africa can be explained by the CAB. A dry climate in central equatorial Africa during a
contemporary wet climate in East equatorial Africa can be explained by a reduced moisture transport
into the continent, caused by the CAB (Tierney et al., 2011). Due to its location east of the CAB (see
fig 1.2 A), the influence of Atlantic-Ocean moisture is minimal in Lake Challa.
Figure 2.3.: Position of the ITCZ during January, April, August and November. Monthly precipitation (based on gauge data) is indicated in
green with contours intervals of 50 mm. Wind fields for the 925 hPa pressure level are indicated with arrows. The arrow length is
proportional to the wind speed. Lake Challa is indicated with a yellow dot. The northeastern monsoonal direction is visible in January, the
southeasterly monsoonal direction in August (http://iridl.ldeo.columbia.edu, from Verschuren et al., 2009).
Chapter III – East African environmental variability
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CHAPTER III. East African environmental variability
3.1. Environmental evolution of equatorial East Africa since the LGM
Several studies concerning the environmental variations in equatorial East Africa during the late
Quaternary were carried out in the last decades. This chapter will summarize the general
environmental evolution for the last 25 ka, roughly starting with the Last Glacial Maximum (LGM).
Figure 3.1 shows a map of East Africa with study locations discussed in this chapter. Table 3.1
contains the name of these locations, the coordinates and the reference paper.
Figure 3.1.: Map of East Africa and the different study sites cited in this chapter. The yellow dot C indicates the location of Lake Challa.
Satellite image from OpenAerialMap.
Table 3.1.: Site details discussed in the text and plotted in figure 3.1.
Nr Location Latitude Longitude Reference
1 Lake Malawi 11°41'1.26"S 34°34'29.73"E Barker and Gasse (2003); Nicholson et al. (2013)
2 Lake Masoko 9°20'3.17"S 33°45'18.41"E Barker and Gasse (2003); Garcin et al. (2007); Kiage and Liu (2006)
3 Lake Rukwa 7°55'31.68"S 32°06'58.56"E Barker and Gasse (2003); Kiage and Liu (2006)
4 Lake Manyara 3°35'34.43"S 35°49'13.66"E Barker and Gasse (2003)
5 Mt. Kenya 0° 09'0.00"S 37°19'0.00"E Barker et al. (2001); Kiage and Liu (2006)
Chapter III – East African environmental variability
9
6 Lake Albert 1°42'2.71"N 30°57'51.60"E Beuning et al. (1997); Kiage and Liu (2006)
7 Lake Kivu 1°58'46.71"S 29°09'29.31"E Gasse (2000)
8 Lake Victoria 1° 04'26.49"S 33°00'55.68"E Gasse (2000); Kiage and Liu (2006)
9 Lake Magadi 1°53'43.61"S 36°14'44.32"E Gasse (2000); Roberts et al. (1993)
10 Lake Naivasha 0°45'57.24"S 36°20'57.45"E Gasse (2000); Kiage and Liu (2006); Verschuren et al. (2000)
11 Lake Nakuru 0°21'45.89"S 36°05'22.34"E Gasse (2000)
12 Lake Elmenteita 0°26'31.24"S 36°14'32.46"E Gasse (2000)
13 Lake Turkana 3°41'5.19"N 36°04'2.53"E Gasse (2000); Kiage and Liu (2006)
14 Lake Tanganyika 6°21'6.06"S 29°36'22.63"E Gasse (2000); Kiage and Liu (2006); Nicholson et al. (2013); Tierney and Russell (2007); Tierney et al. (2008, 2010)
15 Lake Mahoma 0°21'48.83"N 29°53'0.83"E Kiage and Liu (2006)
16 Kamiranzovu 2°29'35.31"S 29°08'46.52"E Kiage and Liu (2006)
17 Mt Kilimanjaro 3° 04'2.73"S 37°21'20.26"E Kiage and Liu (2006); Schüler et al. (2012)
18 Lake Simbi 0°22'5.84"S 34°37'45.69"E Kiage and Liu (2006)
19 Sacred Lake 0° 02'52.28"N 37°31'39.95"E Kiage and Liu (2006)
20 Lake Bogoria 0°15'53.42"N 36°06'0.92"E Kiage and Liu (2006)
21 Loboi Swamp 0°23'31.00"N 36°02'43.00"E Kiage and Liu (2006)
22 Cherangani Hills 1°15'5.75"N 35°27'1.87"E Kiage and Liu (2006)
23 Lake Kimilili 0°57'41.43"N 34°35'15.29"E Kiage and Liu (2006)
24 Lake Abiyata 7°36'33.81"N 38°35'59.51"E Kiage and Liu (2006)
25 Lake Emakat 3°11'35.82"S 35°32'11.86"E Ryner et al. (2007)
The LGM coincides with a period of minimal Northern Hemisphere summer insolation (see fig 3.2),
resulting in a reduced NE monsoonal circulation as well as dry and cold conditions in equatorial East
Africa. Several lakes experienced severe low stands during the LGM due to the weaker global
hydrological cycle, as evident in Lake Tanganyika (fig 3.1, nr. 14), Lake Albert (6) and Lake Victoria (8)
(Gasse, 2000). However, since the precessional-driven summer insolation values are in antiphase
between the Northern and Southern Hemisphere (Berger, 1978), Southern Hemisphere summer
insolation reached a maximum during the LGM. Hence, monsoonal circulation was expected to be
enhanced in the Southern Hemisphere during the LGM. Sedimentological, hydrological and
palynological observations in the southern East African tropics however contradict this hypothesis by
also showing indications for a dry and cold LGM in these areas (Barker and Gasse, 2003; Gasse, 2000;
Kiage and Liu, 2006). Barker and Gasse (2003) suggest that the dry conditions during the LGM can be
explained by low SSTs and the presence of ice sheets in the Northern Hemisphere, having a more
dominant effect on the East African climate system than insolation-induced monsoonal precipitation.
After the LGM, the climate remained rather cool with episodes of prolonged desiccation causing
further low stands of the tropical East African lakes at the beginning of the deglacial period (Beuning
et al., 1997; Kiage and Liu, 2006). Palynological data from Mt. Kilimanjaro (17) however indicate a
shift towards more humid conditions (Schüler et al., 2012), which points out a contradictory signal
between different proxies. Between 17 and 15 ka ago, a wetting/warming phase was established in
equatorial Africa, although the exact onset of this phase is still much debated (Gasse, 2000; Schefuß
et al., 2005). Tierney et al. (2010) detected a rise in land surface temperatures shortly after the LGM,
using molecular proxies and pollen assemblages from Lake Tanganyika (14), reflecting changes in
vegetation cover. This rise in temperature coincides with an increase in Northern Hemisphere
summer insolation, although the exact cause is still uncertain (Tierney et al., 2008). Hydrological
Chapter III – East African environmental variability
10
changes occurred around 15 ka, with a rather drastic transition from arid to humid conditions. As a
consequence of this transition, lake levels in equatorial East Africa rose, as evident in Lake Albert (6),
Lake Emakat (25) and Lake Tanganyika (14) (Gasse, 2000; Ryner et al., 2007; Tierney et al., 2010).
During Northern Hemisphere cold events like the Younger Dryas (ca 12.9 - 11.7 ka BP) and Heinrich
event 1, wind-driven mixing in East African lakes was reduced. This was most likely the effect of a
southern displacement of the ITCZ and a weakened NE monsoon (Tierney and Russell, 2007). Further
these cold spells were shown to be generally arid as a result of a lower Indian Ocean SST (Schefuß et
al., 2011). Low lake levels were observed during the Younger Dryas in Lake Kivu (7), Lake Victoria (8)
and Lake Magadi (9) (Gasse, 2000; Schefuß et al., 2005; Talbot et al., 2007). Garcin et al. (2007) and
Roberts et al. (1993) issued that the NE monsoonal system recovered rapidly at the end of the
Younger Dryas, as evident from climate records of Lake Malawi (1) and Lake Masoko (2). This
resumption of the NE monsoonal system also implied more pronounced migrations of the ITCZ over
the African continent, as described by Garcin et al. (2007).
The early- and mid-Holocene (roughly from 11 - 5 ka BP) in Northern and Eastern Africa were
characterized by extremely humid conditions, with more precipitation compared to modern times
(Tierney et al., 2011a). This period is known as the African Humid Period (AHP) and is generally
assumed to be the result of increased summer insolation (DeMenocal et al., 2000). Whereas the
causing dynamics in Northern and especially Northwestern Africa are relatively well known, the
underlying mechanisms in East Africa, where a similar trend to more humid conditions were shown,
are less understood. Tierney et al. (2011) issued that the East African Humid Period was most likely
the consequence of a reduced precipitation seasonality, caused by an orbitally-induced increase in
precipitation during the dry season. Evidence for the warm and moist conditions during the early and
mid-Holocene is found in pollen assemblages from the sedimentary record of Lake Turkana (13), Lake
Victoria (8) and Lake Naivasha (10) and in vegetation changes on Mt Kilimanjaro (17) (Kiage and Liu,
2006; Schüler et al., 2012). In equatorial East Africa, a high precipitation/evaporation ratio was
reached during the early Holocene as evident in a diatom record from Lake Victoria (8). From the
mid-Holocene until today, precipitation gradually lowered (Gasse, 2000). The transition from a humid
early Holocene to a drier late Holocene occurred stepwise according to Jung et al. (2004), with a first
aridification step at 8.5 ka and a second step from 6 to 3.8 ka, which marked the end of the AHP.
Thompson et al. (2002) described ice core records from Mt Kilimanjaro (17), which reveal three
abrupt climate events at 8.3 ka, 5.2 ka and 4 ka. The event at 8.3 ka reflects a period of strong aridity,
which resulted in a rapid drop of East African lake levels. This event is coincident with decreasing
methane concentrations observed in Greenland ice cores, suggesting that these two events were
closely linked to each other (Gasse, 2000). At 5.2 ka, an abrupt cooling event occurred, which is
recorded in the ice cores by a change in oxygen isotopes. Extremely cold and dry conditions at 4 ka
resulted in the deposition of a dust layer in one of the ice cores. However, due to the higher
resolution of the ice-core record these findings could not be confirmed by other studies so far (Kiage
and Liu, 2006).
Nicholson et al. (2013) describe the temperature variations that occurred over the African continent
in the last two millennia. Records from Lake Tanganyika (14) shows evidence for warm conditions
during the Medieval Climate Anomaly (MCA), which corresponds to the period AD 900 to AD 1200
(Jones et al., 2001). The highest temperatures were reached during the late MCA, roughly 1100 years
Chapter III – East African environmental variability
11
ago. This warmer period was followed by a cooling during the Little Ice Age (LIA), as evident from
palynological data and organic biomarkers from Lake Malawi (1). The LIA corresponds with the
period spanning from AD 1550 to AD 1900 (Jones et al., 2001). Since the last ~250 years, a gradual
warming trend is clearly evident in the climate records, although it was interrupted by a short cooling
event during the mid-20th century. Temperature variations Lake Naivasha (10) during the last
millennium indicate drier conditions during the MCA and wetter conditions during the LIA.
Furthermore, the MCA seems to be coeval with a phase of high solar radiation, while wetter periods
are coeval with periods of low solar radiation (Verschuren et al., 2000).
3.2. Lake Challa proxies
A lot of studies have already been performed on Lake Challa and its sedimentary infill during the last
couple of years, mainly in framework of the CHALLACEA project (Kristen, 2010; Moernaut et al.,
2010; Verschuren et al., 2009). This section will discuss studies that are relevant for this dissertation,
since some data and interpretations from these studies will be used later.
In 2003 a high-resolution seismic survey was performed in order to investigate the sedimentary infill
of the lake (Moernaut et al., 2010). The seismic-stratigraphic data was used to define the coring
location of the CHALLACEA core. The seismic data of Lake Challa were further used to reconstruct
lake-level fluctuations over the last 140 ka. Uniformly draped sediments are considered to be
deposited during periods were the lake level was high, while sediment packets which were deposited
during low lake-level stands are considered to be more concentrated at the centre of the basin, in
the deeper parts of the lake. The reconstructed lake-level fluctuations reflect the moisture-balance
variations caused by environmental variations in equatorial East Africa. Lake Challa experienced
some major episodes of desiccation, but never dried out completely, providing therefore one of the
few continuous paleo-records from equatorial East Africa. The most important lake level variations
since the LGM are shown in figure 3.2b and are discussed below.
A long period of high lake levels persisted in Lake Challa from ~97 ka BP until ~20.5 ka BP. During the
LGM and the beginning of the late-glacial period, the lake level was generally low (fig 3.2), although
periods of more severe low stands had occurred before in the lake (Moernaut et al., 2010). The LGM
related low stand was present until ~14.5 ka BP, with an extreme drought period between ~16.9 and
16.3 ka BP, corresponding to the H1 event. The lake level generally remained high during the last
14.5 ka, except for a few episodes during which the lake levels dropped: from ~12.9 – 12.0 ka BP,
corresponding to the Younger Dryas period, and some mid-Holocene low stands, corresponding with
droughts described by Barker et al. (2001) on Mt. Kenya.
In 2005, in framework of the CHALLACEA-project, gravity cores with a undisturbed sediment-water
interface were recovered from the centre of the lake (fig 2.2 A), together with three parallel piston
cores using a UWITEC hammer-driven piston coring platform. Overlapping successions in the
sediment piston cores were cross-correlated with each other in order to create a composite core.
The CHALLACEA composite core has a total length of 21.6 meter and is now stored in the Ledeganck
complex of Ghent University (Department of Biology – Limnology group). The core sediments are
mainly composed of finely laminated organic mud, alternating between dark and light colors and rich
in diatom silica. Five turbidites are present in the core that consist of reworked crater slope material.
They are situated at 4.87-5.13 m, 6.77-7.09 m, 18.99-19.04 m, 19.18-19.24 m and 20.24-20.39 m core
depth.
Chapter III – East African environmental variability
12
Figure 3.2.: Comparison of Lake Challa records and climate data for equatorial East Africa. Green bars correspond with Northern Hemisphere high-latitude influences, blue bars with Southern Hemisphere high-latitude influences. YD: Younger Dryas, ACR: Antarctic Cold Reversal, H1: Heinrich event 1, LGM: Last Glacial Maximum. a) Rainfall reconstruction at Lake Challa based on the BIT-index variations. The bold line is the three-point moving average (modified from Verschuren et al., 2009). b) Reconstructed lake-level fluctuations based on the seismic-stratigraphic survey from Moernaut et al. (2010). c) Insolation values at the equator during March and September (Berger and Loutre, 1991).
An age-depth model for the CHALLACEA core was established by Blaauw et al. (2011), shown in figure
3.3. It was derived from AMS 14C analysis of 164 bulk organic carbon samples, combined with 210Pb
dating of recent sediments. The ~22 m long core has an age of 25000 years. The age-depth model
was corrected for reservoir ages by analyzing the difference between 14C ages of bulk organic carbon
and the derived age from the 210Pb chronology in that sediment interval, and by wiggle-matching
sequences of bulk-organic 14C dates. The carbon reservoir age evolves from ~450 years during the
LGM towards ~200 years in the early and middle Holocene and ~250 years today. The age-depth
curve was smoothed using a smooth spline function.
Chapter III – East African environmental variability
13
Figure 3.3.: Age-depth model for the CHALLACEA core, based on AMS 14C dating on 164 bulk organic carbon samples. Grey areas indicate the turbidite levels (modified from Blaauw et al., 2001).
The observations described by Moernaut et al. (2010) are supported by the study of Verschuren et al.
(2009), who measured the branched and isoprenoid tetraether index (BIT-index) on the Challa
sediments. The BIT-index is an organic biomarker which is a proxy for local monsoonal rainfall. Higher
BIT-values represent wetter conditions and increased surface run-off. A good correlation between
the BIT-index and the moisture balance variations is observed. Monsoonal rainfall seems to vary at a
half-precessional cycle (~11,500 years), in phase with orbital insolation forcing. When the summer
insolation gradient between the Northern and Southern Hemisphere reached a maximum, the
monsoons in this area were intensified, resulting in wetter conditions. A minimal insolation gradient
corresponds with drier periods and no strengthening of the monsoons. Intensification of the SE
monsoon is observed from ~16.5 ka BP and continued into the Holocene, although an interruption
occurred during the Younger Dryas period. In general, the BIT-index shows periods of relative
drought from 20-16.5 ka BP and from 8.5-4.5 ka BP.
Other studies on Lake Challa sediments included high-resolution geochemical studies described by
Kristen (2010), measuring the deuterium/hydrogen ratio (δDwax) of higher plant leaf waxes in order to
investigate the influence of the Indian Ocean on the paleohydrology in equatorial East Africa (Tierney
et al., 2011b), measuring variations in varve thickness to research interannual rainfall variability
(Wolff et al., 2011) and comparing sediment trap data with the light-dark laminations to examine
modern seasonality in the lake and how this is reflected into the sedimentary record (Wolff et al.,
2014).
Chapter IV – Material and Methods
14
CHAPTER IV. Material and methods
4.1. Grain-size analysis
This thesis topic aims to identify sub populations of detrital mineral material in the sediments from
Lake Challa. In order to obtain this subpopulations, a high-resolution grain-size analysis was
performed on the ~22 meter long CHALLACEA composite core.
Samples for grain-size analysis were taken at constant 12 cm composite-depth intervals over the
entire core length, with a higher sampling resolution around the Younger Dryas. Turbidite intervals in
the core were skipped. The used sampling resolution is the same as the sampling resolution used for
the BIT-analysis from Verschuren et al. (2009). Appendix A indicates the analyzed samples and their
core depth. Every sample consist of a 4-cm core increment, where the sampling depth is considered
to be the central depth in this 4-cm core increments. The sample name includes the central
composite depth of the 4-cm core increment. For example, sample “CHALLA05- 002” consists of the
core increment from 0 to 4 cm composite depth, whose central value is at 2 cm composite core
depth. Approximately 5 gram of sediment were sampled from the cores, whereof 1 gram of bulk
(wet) sediment was used for the grain-size analysis.
The samples were chemically pre-treated in order to remove organic matter and carbonates. For the
removal of organic matter, the samples were put in 10 ml of distilled water and 2 ml H2O2 (30 %) was
added. The mixture was boiled until the reaction stopped. Distilled water was added to the sample in
order to prevent the sample from drying out while boiling. After boiling, the mixture was filled up
again to 10 ml and put aside to cool down. Removal of calcium carbonate (CaCO3) was done by
adding 1 ml HCl (10 %) and boiling the mixture for one minute on a hot plate. The samples were then
filled up to 100 ml and put aside to settle down. They were decanted when the water was clear. This
procedure of filling the sample and decanting when clear was repeated twice in order to create PH-
neutral values. The procedure for removal of organic material and carbonates that was used is
considered to be the standard procedure for grain-size sample preparation.
The standard procedure to remove biogenic silica from the sediments is by adding 1 ml NaOH (2 N)
to the samples in 10 ml of distilled water and boil the samples for 10 minutes. This standard grain-
size pre-treatment has proven to be insufficient during early tests in the lab for the samples in this
study, due to the presence of high amounts of very resistant diatoms in the Lake Challa sediments.
Treatment of the samples solely by adding NaOH was insufficient to completely destroy the diatoms,
even when more NaOH was added. Treatment by adding NaOH and putting the samples in a hot bath
for 7 hours did remove the diatoms present, but this procedure affected also the clay fraction of the
sediments, which is undesirable when the particle-size distribution is wanted. This method was
ultimately not used to remove the diatoms in the sediment.
For this study, the presence of the resistant diatoms in the lake sediments was a big issue since they
influence the grain-size distribution of the clastic sediment fraction. Consequently, a different
procedure was needed in order to remove the biogenic silica present in the lake sediments. Madella
et al. (1998) described a reliable method to extract opal phytoliths from sediments by using Sodium
polytungstate (Na6(H2W12O40)H20), a non-toxic heavy liquid. Sodium polytungstate (also called LST
Fastfloat) has a density of 2.8 g/ml. For this study, the Fastfloat heavy liquid was diluted with distilled
water until it reached a density of 1.9 g/ml, because the detrital mineral fraction present in the
Chapter IV – Material and Methods
15
sediments have a higher density and the diatom fraction has a lower density. Due to the density
differences, the heavy liquid method will cause the denser detrital mineral fraction to separate from
the lighter biogenic silica fraction.
Before the sample was separated into a light fraction and a heavy fraction using the LST Fastfloat,
removal of clays from the samples is necessary. Clay particles in the Challa sediments have a
relatively low density and would float in the Fastfloat if they are not removed before the heavy liquid
separation. Removal of the clay fraction is based on the method of gravitational settling. After
removal of organic matter and carbonates, the sample was put into a beaker of 250 ml, which served
as an Atterberg column. The beaker was filled up with distilled water until there was a water column
of 10 cm height in the beaker. The clay fraction, which was still in suspension after 116 minutes, was
decanted into a big beaker (1 L). This time interval depends on the height of the water column in the
beaker (10 centimeter height) and on the temperature of the distilled water (21°C), and was
calculated using Stokes’ Law. The decanted fraction is finer than 4 µm, while the coarser/heavier
fraction was settled to the bottom of the beaker. The procedure of clay decanting was repeated four
times in order to be sure that all the clay minerals present in the samples were removed. The beaker
with the decanted clay fraction was put aside to settle. The heavier fraction, which includes both the
detrital minerals and the biogenic silica, was put into a sediment oven to dry at 60°C. When the clay
fraction had settled in the large beakers, the water was decanted until about 200 ml was left. This
remaining 200 ml was centrifuged in order to let the clay particles settle. The samples were
centrifuged at a speed of 2600 rpm for 15 – 20 minutes. Some samples were centrifuged twice
because settling was insufficient after one round of centrifuging. The detrital mineral material was
separated from the biogenic silica using the LST Fastfloat heavy liquid. The general set-up for the
heavy liquid separation is shown in figure 4.1. Fastfloat was added into a glass tap. The dry sample
was homogenized by shaking the vial before pouring it into the fastfloat. Subsequently, the sample
was stirred using a glass rod. The heavier fraction, consisting of the detrital mineral material, sank to
the bottom due to its higher density than the fastfloat density (1.9 g/ml). The biogenic silica has a
lower density than the fastfloat and floated to the top of the liquid. When separation into a heavier
and a lighter fraction had occurred, the tap was opened quickly to let the heavier fraction pass and
immediately closed again. The fraction which escaped from the tap was captured onto a filter with
pore size 12-15 µm. After the fastfloat passed through the filter, the filter was rinsed with distilled
water in order to get all the remaining fastfloat crystals out of the filter. Since LST Fastfloat is an
expensive chemical, every fastfloat crystal needed to be recycled. The lighter fraction, which contains
the diatoms, was captured onto another filter. This filter was also rinsed with distilled water in order
to recover the fastfloat crystals.
Chapter IV – Material and Methods
16
Fig 4.1.: Set-up of the heavy liquid separation method.
When the filter with the heavier fraction was dry, the sediment was added to the clay fraction. The
samples were poured into a 100 ml beaker and 1 ml of sodium hexametaphospate (2%) was added.
This mixture was boiled shortly on a hot plate. Sodium hexametaphospate disintegrates all
aggregates which are present in the samples. After boiling, the samples were put aside to cool down
to room temperature.
Particle-size distributions were obtained with the Malvern Mastersizer 3000, using the principle of
laser diffraction (fig. 4.2). Samples were inserted into the Malvern Mastersizer 3000 using a Hydro
Volume. The principle of laser diffraction is based on the scattering of light when the laser is
obstructed by a particle (i.e. sediment grain in this case). Larger particles scatter the light at smaller
diffraction angles than finer particles, but with a higher intensity. As a result, a variation in light
intensity reaches the detectors. Samples are measured with both a red (633 nm) and blue laser (470
nm), to avoid Rayleigh scattering. Rayleigh scattering occurs when the sediment particles are too
small. If a particle is smaller than 1/10 of the laser wavelength, the laser light will be scattered in all
directions with no angular variation. By using a blue laser, which has a lower wavelength than the red
laser, the Rayleigh scattering will shift to a smaller size. Particle-size distributions are obtained by
measuring the angular variations in light intensity using the Mie-theory of light scattering and are
expressed as the frequency of a certain class weight (http://www.malvern.com, 2016). An incident
laser beam ray can be reflected, refracted or absorbed by the sediment particle, and the Mie-theory
takes all these pathways into account. The grain-size distributions of sediment samples are better
described using the Mie-theory than using the Fraunhofer-theory (Eshel et al., 2004), which only
takes diffraction of the laser beam into account.
Chapter IV – Material and Methods
17
Fig 4.2: Pathways of the red and blue lasers inside the Malvern Mastersizer 3000. Variations in light
intensity reaching the detectors results in the calculation of the grain-size distribution.
Prior every measurement, the device was initialized and the background was measured. The
instrument makes a measurement during the background check. The sample cell is filled with
distilled water during this background check but no sediment is present. Like that the diffraction of
the laser beam caused by the distilled water is determined, which is subtracted from the following
measurement with sediment, resulting in the solely particle induced diffraction. Afterwards, the
sediment sample was carefully mixed and added into the Malvern using a pipette until the laser
obscuration was in range (between 5 and 20%). Three measurements were performed for every
sample. The obtained grain-size distributions were checked visually if they were stable. If the
distributions did not show good overlap, other measurements were performed until the results were
stable.
When all samples were measured, the average grain-size distribution was calculated for each sample.
The calculated average of the different samples was used as an input for the end-member analysis.
The mean grain size was calculated using the GRADISTAT software package v8.0 (Blott and Pye,
2001).
4.2. End-member modelling analysis
The clastic fraction accumulated in aquatic basins consists of a mixture of sediment population
supplied from different sources and are transported by different mechanisms to the site of
deposition (e.g. Weltje and Prins, 2003). This results in often polymodal grain-size distributions,
which are hard to interpret in terms of sediment transport dynamics or paleo-environmental
interpretations. Therefore mathematical-statistical end-member models are frequently applied in
order to define the different sub populations within the sediments (Meyer et al., 2013; Stuut et al.,
2002; Weltje and Prins, 2007). The method aims to establish a physical mixing model that describes
the measured data in a limited number of nonnegative and unimodal sub populations which can be
Chapter IV – Material and Methods
18
individually interpreted. The calculated end members yield important information about depositional
processes and sediment provenance (Weltje, 1997). In this study, unmixing was performed using the
AnalySize modelling algorithm developed by Paterson and Heslop (2015). AnalySize is a free GUI
software package which uses an algorithm inspired by hyperspectral image analysis for unmixing of
grain size distribution (https://github.com/greigpaterson/AnalySize).
When grain-size distributions are imported into AnalySize, the software allows to browse through the
different samples in order to visually check how the grain-size distributions change through the
complete composite core sequence. End-member analysis (EMA) can be performed by a non-
parametric approach or by a parametric approach. The non-parametric approach estimates the end
members from the initial raw data, based on covariability in the grain-size distributions. This
approach gives fast results but is often not able to identify single sediment sources in the data set,
since polymodal or negative end members are obtained. Therefore, Paterson and Heslop (2015)
introduced an alternative, the parametric approach, which unmixes the grain-size distributions into
parametric distributions, therefore being able to identify unimodal grain-size sub populations. The
end members are estimated using a least squares approach and are then fitted to the individual
grain-size distributions. Further explanation about the use of the AnalySize software is given in the
results chapter.
Chapter V - Results
19
CHAPTER V. Results
5.1. Grain-size analysis
The variations in grain size as a function of the downcore composite depth is shown in Fig 5.1.
Generally, the sediment has a silty/clayey texture. The mean grain size is fluctuating between 8 and
15 µm and the dominant mode is situated around 10 µm. The upper 7.5 m and the core interval
between roughly 12 and 17 m have a very fine/fine silty compositions (5-10 µm), which is a slightly
finer grain size compared to the rest of the core, with a fine to medium silty composition (10-15 µm).
Six zones (I - VI) are identified in which the mean grain size remains approximately the same (see Fig
5.1). In the upper 2.5 meter of the core (zone I), the mean grain size is ~10 µm, with an abrupt
increase in grain size at 2.5 m. Zone II is situated between 2.5 – 8 m depth and is characterized by a
slightly finer grain size (mean around 9 µm) with a lower volume density compared to zone I. The
interval between ~8 – 9.5 m (zone III) is characterized by a clearly coarser grain size, with a mean
situated around 13 µm. Zone IV (9.5 – 12 m depth) shows some variability in the grain-size
distributions, with a mean grain size fluctuating between 7 and 12 µm. Between ~12 – 17.5 m (zone
V), the mean grain size remains rather constant, situated around 8 µm. There is only a slight increase
between 16 and 16.5 m depth towards a mean grain size of 10 µm. Zone VI confines the bottom 4 m
in the core and shows a variable grain size with a mean grain size fluctuating between 10 – 14 µm.
The grain-size distributions of 9 samples throughout the composite core are given on the right in
figure 5.1. They support the general observations which are described above. Samples 878, 998, 1754
and 2006 have a mode which is situated between 10 and 15 µm, while the other samples have their
mode situated at finer grain sizes, between 5 and 10 µm. Sample 518 is clearly polymodal, with its
second mode situated at a much coarser grain size around 250 µm. This sample originates from the
base of a turbidite, which might explain the coarser nature. A small peak is observed in all samples
around 0.8 µm, except for sample 878 in which this peak is absent.
Chapter V - Results
20
Figure 5.1: Variations in grain size (in volume %) together with the mean grain size (in µm) for the CHALLACEA core as a function of composite depth. The blue curve represents the age-depth model for the
CHALLACEA core (Blaauw et al., 2011). Grey areas represent the depths of the turbidite levels. The grain-size distributions for 9 samples are shown on the right with indications of their composite depths in cm.
Chapter V - Results
21
5.2. End-member modelling
5.2.1. End-member Analysis (EMA)
In order to unmix the grain-size distributions of the CHALLACEA core, a new end-member model
AnalySize (Paterson and Heslop, 2015) was used. The overlay of all grain-size distributions of the core
(n=178), shown in Fig. 5.2, reveal a polymodal distribution, with 5 recurring modes at ~0.6, 5, 12, 150
and 550 µm respectively.
Figure 5.2.: Multi-specimen plot of all obtained grain-size distributions. Numbers 1 – 5 identify five recurring peaks that are observed in the
entire data set.
In a first step, a non-parametric end-member model was established. The nonparametric EMA
calculates the maximum amount of end members (EM) based on the initial raw data. However, a
non-parametric model can result in negative or polymodal end members and are therefore only used
as a first estimation of the needed end members. Figure 5.3 A shows the goodness-of-fit statistics of
the non-parametric end-member model. Figure 5.3 B shows the end members calculated by the non-
parametric end-member model, in which EM 4 and EM 5 clearly show a polymodal distribution.
Chapter V - Results
22
Figure 5.3.: A) Coefficient of determination (R²) in function of the number of end members for a non-parametric end-member model. R2 is
increasing with increasing amount of end member. B) Non-parametric end-member model for 5 end members.
The coefficient of determination (R²) is calculated to identify the minimal numbers of end members
necessary for a good statistical explanation of the data. The correlation illustrates a better statistical
fit (higher R2) with increasing number of end members (see fig 5.3 A). The R2 for the 4 end-member
model is 0.994, which means that 99.4 % of the variance in each grain-size class can be reproduced.
For models with a higher number of end member, there is only a small increase in R², indicating that
the 4 end-member model provides a realistic resolution and meets the requirement of a minimum
number of end members and maximum reproducibility. The R² for the 5 end-member model is 0.997,
hence 99.7 % of the grain-size distribution can be explained. The 5 end-member model calculated by
the non-parametric EMA is shown in figure 5.3 B. However, since polymodal end members are
obtained by the non-parametric approach (see fig 5.3 B), further analysis was necessary.
In order to verify the initial amount of end members, calculated by the non-parametric EMA, a
parametric end-member model, with a given amount of end members, was performed in a second
step. Parametric end-member modelling takes a longer computation time but generally results in
more reliable results. Fig 5.4 shows the goodness-of-fit statistics for the parametric EMA. Similar to
the results of the non-parametric model R2 is rising with increasing number of end members. The 4
end-member model using a parametric EMA explains 99.0 % of the grain-size distributions, while the
5 end-member model explains 99.3 %.
Chapter V - Results
23
Figure 5.4.: Coefficient of determination (R²) as a function of the number of end members for a parametric EMA. R2 is increasing with
increasing amount of end members.
The overlay of the modeled end members and the measured grain-size data (Fig. 5.5) show that the
end members do not match the entire grain-size distribution. The 4 end-member model (fig 5.5 A)
does not show a good overlap between its third end member (orange curve) and the fourth peak
which was observed in the grain-size distributions as shown in figure 5.2. The overlap in the 5 end-
member model (fig 5.5 B) shows a better overlap, indicating a better model. However, none of the
generated models show any overlap with the first peak in the grain-size distributions which is
situated around a mode of 0.6 µm.
Figure 5.5.: A) Overlay of 4 end members onto the measured grain-size data (grey curves). As obvious from the plot the 4 end members do
not match the full grain-size spectrum. B) Overlay of 5 end members onto the measured grain-size data. Beside of the finest peak the 5 end
members do cover the whole range observed in the grain-size distributions.
Chapter V - Results
24
As a result of these observations, the model resulting in five parametric end members is used for
further interpretation (fig 5.6). The modes of the distinct end members are situated at 4, 10, 20, 60
and 400 µm respectively. The end members are perfectly unimodal and very-well sorted, which is an
indication for a representative model.
Figure 5.6.: Abundance of the five parametric end members used in this study.
5.2.2. End-member variations
Figure 5.7 shows the five obtained end members, modeled onto the grain-size distributions of six
distinct samples. The abundance of each end member varies depending on the shape of the sample
distribution. The samples are situated at 2, 530, 854, 1118, 1718 and 2162 cm composite depth
respectively, and each sample in figure 5.7 represents one of the identified zones I to VI. By
comparing the variations in the end-member abundances of these samples, a general idea is
established on how the downcore variations in end-member abundances are evolving.
Generally, EM’s 1 and 2 are the most important end members, showing high abundances although
some considerable variations are present throughout the core. EM 1 is the most important end
member in zones II, IV, V and VI, while EM 2 has a larger importance in zones I and III. EM 3 is also
prominently present in all samples, and its abundance seems rather stable in each zone. EM’s 4 and 5
represent the coarsest fraction of the distributions, with a generally higher abundance of EM 5. EM 4
is almost absent in zones III and V, and has a rather low abundance in zones IV and VI. However, its
abundance is higher than the abundance of EM 5 in zones I and II. The low abundance of EM 4 in
zones III - VI can probably be explained by the coarser nature of these samples with respect to zones
I and II (upper 7.5 m of the core). This coarser sediments result in an increase in the abundance of
EM 5.
Chapter V - Results
25
Sample CHALLA05-530 (zone II) is situated at the base of the uppermost turbidite in the core, and
therefore also shows increased abundance of coarse material, which is expressed as an increase in
EM 4. Further, sample CHALLA05-854, situated in the clearly coarser zone III shows a much less
pronounced abundance of EM 1, while EM 2 has its highest abundance in this sample.
Figure 5.7.: Modelling of the five obtained end members onto the grain-size distributions of six samples throughout the core. The core
samples are respectively 2, 530, 854, 1118, 1718 and 2162 cm composite depth. Each sample originates from one of the six different zones
which were identified in the core (Zones I – VI).
Chapter V - Results
26
The variations of the end member abundances through time are shown in figures 5.8 and 5.9. Figure
5.8 shows the cumulative proportions of the different EM’s through time, while figure 5.9 shows the
abundances per end member. The curves in figure 5.8 and the bold curve in figure 5.9 represent the
weighted averages for the different EM’s in order to better visualize the temporal variations. EM’s 1
and 2 are most dominating and together represent 70-80 % of the grain-size distribution. However,
their abundances varies significantly through time. The occurrence of EM’s 3 and 5 show less
variation and remain rather constant through time. EM 4 generally has a larger contribution to the
grain-size distributions during the last 11 ka. Its abundance during the period 11 – 25 ka is generally
very low and sometimes almost absent. Similar to the results of the mean grain size (fig. 5.1) the six
zones can be identified in the end-member abundances as well.
Figure 5.8.: Proportions of the different end members as a function of time. The curves represent the weighted averages of the
abundances. The different zones which were identified in the sediment core are indicated with numbers I – VI.
Zone I represents the period from 0-2.7 ka. In this period, EM 2 is most abundant while the frequency
of EM 1 increases from ~28 % to ~45 % (fig 5.8). The abundance of EM 2 shows two episodes of
reduction during this time interval, the first around 0.5 ka and a second between roughly 2 and 3 ka.
The second reduction episode is also illustrated in EM 1. EM 4 had two periods of increased
abundance, the first between 0 and 0.5 ka and the second from 2 to 2.7 ka (fig 5.9). The abundance
of EM 5 gradually increases from ~2 % to ~8 %.
Chapter V - Results
27
The period between 2.7 and 9.5 ka (zone II) features an gradual increase in abundance of EM 1 from
~45 % to 60 %, followed by a decrease towards ~45%. The maximal abundance of ~60 % is reached at
5.5 ka. The decrease in the abundance of EM 1 starts abruptly after its maximum and rose again at
6.5 ka to ~55 % (fig 5.8). Between 6.5 ka and 9 ka, its abundance generally decreased, although not
gradually but with some fluctuations. The abundances of EM’s 2, 4 and 5 remained rather constant in
this zone, although EM’s 4 and 5 reach higher abundances during the interval 5.5-6.5 ka, coincident
with a decrease in the abundances of EM 1 and 3 (fig 5.9).
Between 9.5 and 11.5 ka, EM 1 reaches an absolute minimum of ~15 %. This interval corresponds to
zone III in the sediment core, which is characterized by coarser sediments (fig 5.1). However, this
coarser interval does not show an increase in the coarser end members (EM 4 and 5), but rather
shows an prominent increase in EM’s 2 and 3 (fig 5.9). EM 2 increases from 18 % at the end of zone II
(9 ka) towards 60 % at 10.5 ka. EM 3 shows a similar increase, from 6 % at 9 ka towards 20 % at 10.5
ka. A slight increase is observed in the abundances of EM 4 and 5 during the period 11-11.5 ka.
Zone IV runs from 11.5 to ~15 ka. Similar to zone II, EM 1 represents around 50 % of the grain-size
distribution. However, from 13 to 14.5 ka, a significant decrease is present in the abundance of EM 1
(fig 5.8), which results in an increase in EM’s 2 and 3. End member 4 almost completely disappears
during this period, with an abundance of ~2 %. EM 5 remains constant around ~5 %.
The subsequent interval, between ~15 and ~20.7 ka (zone V), is featured by the highest abundances
of EM 1, up to 70 %, although values are decreasing around 19 ka. EM 2 reaches a minimum during
this period, EM 3 increases to ~12 %, while the other EM’s show little variation. Around 20.5 ka, a
severe decrease of EM 1 from ~65 % towards ~35 % is observed. The abundance of EM 2 increases
significantly from ~20 % towards ~45 % at this time. EM 4 remains low at ~2 %.
In the period from ~20.7 ka until 25 ka, which represents zone VI, the abundances of EM’s 1, 4 and 5
remain rather constant, with several short-term variations. EM 1 does show some fluctuations, with
an increase and decrease in its abundance between 21-22 ka, followed by a gradual increase from
~30% at 22 ka to ~40% at 25 ka. EM 4 becomes slightly more important between 21.5 and 22.5 ka,
but further remains its relatively low abundance. EM 2 varies between 40 % and 55 %, with a
decreasing trend from 23 to 25 ka. EM 3 gradually lowers towards 2 % at 22 ka, and increases again
afterwards to 12 %.
Chapter V - Results
28
Figure 5.9.: Abundances of the five end members as a function of time. The bold curve represents the weighted average. The identified
zones are indicated with numbers I – VI.
Chapter VI - Discussion
29
CHAPTER VI. Discussion
6.1. Identification of the end members
Based on their distinct characteristics, the correlations between the end-member abundances and
different proxies, an explanation what the different end members represent was established. Figure
6.1 compares the abundances of end members 1, 4 and 5 with the BIT-index from Verschuren et al.
(2009), the lake level fluctuations in Lake Challa from Moernaut et al. (2010) and insolation values at
the equator during March and September (Berger and Loutre, 1991). The BIT-index is used as a proxy
for local monsoonal rainfall, with higher values representing periods of increased humidity and
increased surface run-off. Identification of each end member is explained below and subsequently
used for a paleo-environmental interpretation.
Figure 6.1.: Comparison of the end-member abundances (weighted average) with insolation values at the equator during March and
September, the BIT-index and lake level fluctuations in Lake Challa. Numbers I-VI represent the different zones which were identified in the
grain-size variations. The limits of these zones are indicated with dotted lines. Gray bars indicate drought events in East Africa: EAD: East
African droughts, YD: Younger Dryas, LGM: Last Glacial Maximum. The green lines indicate the ages of the turbidite levels in the
CHALLACEA core.
Chapter VI - Discussion
30
6.1.1. End member 1
End member 1 corresponds with the finest fraction which is present in the sediments, with a mode
situated at 4 µm. With a percentage of 15-80%, it is the most abundant end member in the record.
Comparison of EM1 and the grain-size distribution of shortcores from Lake Challa (Eloy, unpublished
MSc thesis) shows a good overlap (fig 6.2). EM 1 shows an inverse correlation with the BIT-index and
the lake levels stands, with an increased amount of EM 1 during periods of low lake levels and vice
versa (fig 6.1). Based on these observations, EM 1 is concluded to represent the fine-grained
background sedimentation of Lake Challa. A drop of the lake level during more arid times results in a
larger catchment area and more erosion as well as more available sediments, leading to an increase
of clastic material entering the lake. The fine clayey material stays in suspension and only deposits
slowly, allowing this sediment fraction to reach the center of the lake.
Figure 6.2.: Identification of end member 1 (blue curve) by comparison with grain-size distributions from shortcores (grey curves) in Lake
Challa (after Eloy, unpublished MSc thesis).
6.1.2. End member 2
The second end member has a mode of 10 µm. As evident from Figure 6.3, there is a good
correlation between end member 2, the BIT-index and the lake-level variations. A higher abundance
of EM 2 is present during periods of increased humidity and vice versa. Microscope pictures of
distinct samples revealed the presence of diatoms in the samples next to clastic particles (see fig 6.5),
which indicates an insufficient working of the heavy liquid separation method.
Chapter VI - Discussion
31
Figure 6.3.: Comparison of the abundances of EM 2 and EM 3 with the BIT-index and lake-level fluctuations in Lake Challa. The bold line in
the end-member curves represents the weighted average. The identified zones are indicated with numbers I – VI.
Two dominant diatom species are present in the Lake Challa sediments, Nitzschia sp. 1 and
Gomphocymbella sp. 1 (Milne, 2007). The size of these species varies between 10 µm and 30 µm.
Due to their slim and elongated shape the grain-size measurements will give instable results.
Depending on their position in the laser beam the result will over- or underestimate the real particle
size, leading to intermediate grain size (fig 6.4). Based on the good correlation between the
hydrological fluctuations and the abundance of EM 2, this end member is concluded to represent the
diatom signal from the species with a size of 10 µm (Nitzschia sp. 1). Periods of higher precipitation
increased the nutrient concentrations in the lake, and therefore resulted in an increased diatom
productivity (Milne, 2007). Since the focus in this dissertation is on the siliciclastic fraction in the
sediments and not on the biogenic fraction, EM 2 was excluded from further interpretation.
Chapter VI - Discussion
32
Figure 6.4.: Sketch illustrating the variable particle size of diatoms in the Malvern Mastersizer, depending on their position in the laser
beam. A: small particle size measured, B: intermediate particle size measured, C: larger particle size measured.
6.1.3. End member 3
End member 3 has a mode situated at 20 µm. The abundance of EM 3 show variations which are very
similar to the variations of EM 2, with higher abundances of EM 3 observed during wetter periods
and vice versa (see fig 6.3). Based on the large similarities with EM 2, EM 3 is suggested to represent
a second diatom signal. Periods of low lake level stands most likely enhanced mixing of the water
layers in the lake, resulting in enhanced nutrient supply in the deeper parts of the water column. An
increased mixing during these periods results in the dominance of Gomphocymbella sp. 1 diatoms
(Barker et al., 2013), which are larger in size than the Nitzschia sp. 1 diatoms. This explains the higher
abundance of EM 3 in zones II and V. The mode of 20 µm matches with the size of the diatoms as
described above, and therefore EM 3 is concluded to represent the diatom signal from the larger-
sized diatoms (Gomphocymbella sp. 1). The high abundance of diatoms in the samples, as evident
from the microscope pictures (fig 6.5), support this conclusion. EM 3 is also not used for further
interpretation.
Chapter VI - Discussion
33
Figure 6.5.: Microscope images for six distinct samples in the CHALLACEA core, which revealed the presence of diatoms (D) next to clastic
sediment particles (C). Each sample is coming from a different zone (Z I – VI) in the core.
6.1.4. End member 4
The mode of end member 4 is situated at 60 µm. The signal of this EM is rather complex. During the
Pleistocene, the abundance is moderately low (1-6 %), while in the Holocene the abundance is more
pronounced including several distinct maxima (up to 18 %). Correlation with BIT and lake-level
fluctuations is generally good, except in zone III. Transitions from low to high lake levels are indicated
by a low abundance of EM 4. Increasing humidity, evident as a rise in BIT-values or lake level, is
followed by an increasing abundance of EM 4. Correlation with BIT-results revealed that peak
Chapter VI - Discussion
34
abundances are reached during periods of maximal humidity. However, the maximal abundance of
EM 4 (8-9 ka) is not reached during a period of maximal humidity, but rather in a period towards
more arid conditions. An abrupt rise in the abundance of EM 4 is observed after drought periods in
equatorial Africa (fig 6.1). A maximum is immediately present after the Younger Dryas and the East
African droughts, while a post-LGM maximum was only established after ~0.5 ka. A comparison of
EM 4 with the grain-size distribution of onshore samples from Lake Challa (Eloy, unpublished MSc
thesis) show a good overlap with a distinct peak around 60 µm (fig 6.6). This indicates that this end
member is most likely originating from this source area. Based on the described observations, EM 4 is
concluded to represent proximal aeolian dust. However, since there is no excessive amount of data
available from possible dust source areas near Lake Challa, future sampling in possible source areas
should strengthen this interpretation. Furthermore, the deposition of wind-blown sediments in the
lake shows a monsoonal signal, with stronger monsoons resulting in a higher sedimentation rate of
aeolian dust. This can be explained by the dry monsoonal winds in East Africa. As described in
chapter II, passage of these winds above the eastern Sahara and friction with the East African
shoreline results in a decreasing humidity of the monsoonal winds (Nicholson, 1996). However, still
some moisture remains present in the winds, so that stronger monsoons also result in increased
humidity. This explains why an increase in wind-blown sediments is observed during moist times. The
link between aeolian dust in Lake Challa and the monsoons will be described more into detail below.
Figure 6.6.: Identification of EM 4 (orange curve) by comparison with grain-size distributions of onshore samples from Lake Challa (grey
curves). The inset shows the locations of the onshore samples (yellow dots) with respect to the lake (grey area) and the lake catchment
area (dotted line).
Chapter VI - Discussion
35
6.1.5. End member 5
End member 5 corresponds with the coarsest fraction in the sediments, with a mode situated at 400
µm. The abundance of this end member shows some variation through time, however a correlation
with the BIT-index and lake-level fluctuations is not evident (fig 6.1). Higher abundances are generally
observed during transitions towards lower lake levels and during periods of increased rainfall.
However, the high abundances are generally only lasting for a short amount of time (~1000 yr).
Correlation with onshore samples from the crater rim of Lake Challa (Eloy, unpublished MSc thesis)
show a strong overlap between EM 5 and the grain-size distributions of the onshore samples coming
from the crater rim (fig 6.7). EM 5 is therefore concluded to represent erosional material from the
crater rim of the lake. The coarser nature of this material is explained by the close proximity of the
source area. The sediment is only transported to the center of the lake under special conditions, e.g.
during transitions of lake level stands or by collapsing of the crater rim when the lake level was high.
These periods are characterized by an increased transportation energy, and therefore allow the
coarse particles to reach the center of the lake.
Figure 6.7.: Identification of EM 5 (blue curve) by comparison with grain-size distributions of onshore samples (grey curves) from the crater
rim of Lake Challa (after Eloy, unpublished MSc thesis). The inset shows the locations of the onshore samples with respect to Lake Challa.
Chapter VI - Discussion
36
Correlation between EM 5 and the turbidite intervals gives an insight in the erosional dynamics that
occurred during the last 25 ka. The turbidites in the core were not sampled for grain-size analysis, so
no information is presented about them in the figures. However, an increasing abundance of EM 5 is
observed in the periods leading to the age when a turbidite was deposited (5.9, 8, 22.2 and 23.4 ka
respectively). Correlation with the lake-level fluctuations indicate that turbidites were triggered
during transitions from a high to a low lake level (see fig 6.1). A drop in lake level exposed the
sedimentary material on the edges of the lake. As evident from the bathymetry and seismic profiles
of Lake Challa (Moernaut et al., 2010), the upper slopes are dipping between 30° and 90° (see fig
2.2), resulting in an unstable ground when exposed. Abundance increase of EM 5 in the period
leading to a turbidite is interpreted as build-up of slope instabilities in the crater rim, which
ultimately led to triggering of the turbidites. After deposition of the turbidite, the abundance
abruptly decreased.
6.2. Paleo-environmental implications of the dust fraction
The low abundance of the aeolian fraction (EM 4) during the Pleistocene, followed by an increased
abundance in the Holocene, is interpreted as reflecting the monsoonal signal in equatorial Africa,
rather than reflecting lake level changes or increasing run-off. Aeolian sediments are deposited
during the dry season of a monsoonal cycle, with an increased dust input during periods of a
strengthened monsoon.
In the period corresponding with zone VI (20.7-25 ka), insolation on the equator was maximal during
the summer months (see fig 6.1). During this period the ITCZ was located north of Lake Challa,
resulting in an enhanced SE monsoon. An increased abundance of EM 4 is observed between 21.7
and 22.7 ka. Barker et al. (2011) described a period of reduced monsoonal rainfall in Lake Challa
between 22 and 25 ka, based on oxygen isotopes from biogenic silica in the sediments. However, the
observations from Barker et al. (2011) are contradictory with the BIT and lake level fluctuations,
which indicate a rather humid period. A prolonged dry season is assumed during this interval, due to
a reduction of the long rains linked to a weak SE monsoon during this interval. The longer-lasting dry
season of the monsoon resulted in an increasing dust deposition in Lake Challa.
During the late Pleistocene (zones IV and V), maximal insolation at the equator occurred during the
winter months. The ITCZ moved southward, resulting in a dominance of the NE monsoonal system.
As described in chapter III, the NE monsoonal system was weakened during the LGM and YD, most
likely because Northern Hemisphere high-latitudinal ice sheets and the Indian Ocean SST had a
dominant influence over the African monsoonal system (Barker and Gasse, 2003; Tierney and Russell,
2007). This is reflected in the low abundance of EM 4, which shows little input of aeolian sediment in
the lake during these periods due to the reduced monsoonal activity.
At the beginning of the Holocene (zone III), the NE monsoonal system regained strength. An abrupt
resumption of the monsoon activity is described by Garcin et al. (2007) during the transition from the
YD to the Holocene. The abundance of EM 4 increases after the YD, although not very significant.
These observations are supported by the study from Weldeab et al. (2014), who reconstructed the
evolution of the East African monsoonal strength during the Holocene. They describe a gradually
increasing monsoonal strength during the early Holocene, which is in agreement with the increasing
input of aeolian sediments during the period from ~11.5 ka to ~9.5 ka (fig 6.1). Weldeab et al. (2014)
and Jung et al. (2004) further described that the monsoonal strength gradually decreased from 8.7 ka
Chapter VI - Discussion
37
onwards. The maximal abundance of EM 4 is reached at ~9 ka, which indicates a good correlation
with the described monsoonal evolution.
The mid and late Holocene (zone I and II) are characterized by a maximal insolation during the
summer months. Hence, the ITCZ was situated north of Lake Challa. The SE monsoonal system was
dominant during this interval. Consequently, the aeolian input in Lake Challa was decreasing due to
the weakening of the SE East African monsoon. During the last 5 ka, similar conditions were present
as during zone VI, with a reduced long rain season resulting in a longer dry season (Barker et al.,
2011). This is reflected in the abundance of EM 4, with a higher aeolian input during the last 5 ka (fig
6.1).
Since the aeolian sediment in Lake Challa has a rather coarse grain size of about 60 µm, the dust
source must be situated close to the lake. The most likely dust sources are situated to the
northeastern and northwestern side of the lake. The onshore samples in which overlap is observed
with EM 4 are situated to the south-southeastern side of the lake and in the northwestern side (see
fig 6.6). The wind in this area is dominantly
coming from the southeast and the
northeast. Consequently, dust is more
likely to come from these directions. The
aeolian dust fraction in the onshore
samples is blown in by the southeastern
monsoonal winds, onto the southwestern
crater rim, in the lake and over the lake
onto the northwestern side. Figure 6.8
compares a vegetation map from the area
(Sinninghe Damsté et al., 2011) with
satellite imagery (Google Earth). At the
western side of the lake, the montane
forests of the Mt Kilimanjaro and other
vegetation types cover main parts of the
surface, reducing possible dust source
areas. At the eastern side of the lake the
vegetation consists of an savanna
landscape with open bush- and grassland.
This type of patchy vegetation allows
particles to be lifted up and transported by
wind. Moreover, as visible in figure 6.8,
rivers are present in this area. Since it is
known that dried out- lake or river beds
are an important source for aeolian
material (Washington et al., 2003), these
rivers and their catchments would provide
a good source of dust, during periods with
low precipitation. Figure 6.8.: Comparison of a vegetation map from Lake Challa (Sinninghe
Damsté et al., 2011) with a satellite image (Google Earth) from the lake in
order to pinpoint the dust source areas.
Chapter VII - Conclusions
38
CHAPTER VII. Conclusions
This study regarded the terrigenous fraction from the sedimentary infill of Lake Challa
(Kenya/Tanzania). A high-resolution grain-size analysis on the CHALLACEA composite core was
carried out using laser diffractometry. Due to very large abundance of diatom frustules in the
sediment, pre-treatment of the samples was done using a heavy liquid separation technique
(Madella et al., 1998). Downcore grain-size variations allowed to distinguish six different zones which
share the same characteristics. These zones show good correlation with the already available proxies,
like the lake-level fluctuations and the BIT-index (Moernaut et al., 2010; Verschuren et al., 2009). The
obtained grain-size distributions were unmixed into geologically representative end members in
order to gain insights about the mechanisms that transported siliciclastic particles to the lake and
how their variation through time was influenced by prevailing climate conditions.
Five end members were identified after end-member modeling. The first end member represents
clayey background sedimentation and shows good correlation with BIT and lake-level fluctuations.
Higher abundances are observed during arid periods with low lake levels, and an enlarged catchment
area, resulting in increased input of clastic material. Sedimentation of clayey material is the most
important sedimentation mechanism, except during the interval 11.5 – 9.5 ka.
Two diatom end members are identified, implying an unsatisfactory working of the heavy liquid
separation method. The finer-sized end member is interpreted to represent the smaller diatom
fraction (Nitzschia sp. 1), while the slightly coarser-sized end member most likely represents larger
diatom species (Gomphocymbella sp. 1). Increased precipitation (high lake levels) enhances nutrient
input in the lake, resulting in diatom blooms.
The fourth end member represents the aeolian fraction in the sediments. A monsoonal signal is
recorded in this sediment fraction. Deposition of wind-blown sediments occurs during the dry season
of a monsoon, with increased aeolian input during periods of stronger monsoons. In general, dust
input was more important during the Holocene than during the Pleistocene, indicating that the
monsoonal system in equatorial East Africa increased in strength following the Younger Dryas.
Periods of weakened NE monsoons are observed during the LGM and YD, as evident from a low dust
input. A transitional interval is present from 11.5 to 9.5 ka, during which the monsoonal system
gradually gained strength. During the middle and late Holocene, the SE monsoonal strength initially
decreased, but an increased dust input is observed during the last 5 ka when the dry season of the
monsoon was prolonged. The dust fraction in Lake Challa sediments is rather coarse (~60 µm) and
therefore the provenance of this fraction must be situated close by the lake. Due to the prevailing
wind direction and the availability of the dust sources, aeolian transport is suggested to come
predominantly from the eastern-southeastern side of the lake.
End member 5 is representing run-off of coarse erosional material, originating from the crater rim.
Increasing abundances are observed during transitions from high to low lake levels, since lake level
lowering exposes the steep crater rim and causes instabilities. Moreover, increasing abundances are
observed in periods leading to the deposition of turbidites, which points to build-up of slope-
instabilities and ultimately failure of the rim. This depositional mechanism remains equally important
through time and is the second most important mechanism for transport of clastic material to the
lake.
Chapter VII - Conclusions
39
Future research should include improving the heavy liquid separation technique in order to
completely remove the diatoms which are present in the sediment. The diatoms are probably
obscuring the signal from the terrigenous fraction, therefore making the identification and
interpretation of the end members more difficult. Furthermore, identification of the sediment
provenance could be performed by combining XRD-analysis with grain-size analysis from onshore
samples of potential dust source areas. Isotope records and geochemical proxies could be combined
with the already available proxies in order to create an even broader view on the environmental
evolution of Lake Challa.
40
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APPENDIX
Appendix A: List of the grain-size samples, their composite core section and the depth of the
sampled core increment. Black lines indicate the levels of the turbidites between two samples.
Sample name core section
Depth interval (cm comp. depth)
CHALLA05- 002 1G 0-4 CHALLA05- 014 1G 12-16 CHALLA05- 026 1G 24-28 CHALLA05- 038 1G 36-40 CHALLA05- 050 2Ka 48-52 CHALLA05- 062 2Ka 60-64 CHALLA05- 074 2Ka 72-76 CHALLA05- 086 2Ka 84-88 CHALLA05- 098 3PIb 96-100 CHALLA05- 110 2Kb 108-112 CHALLA05- 118 2Kb 116-120 CHALLA05- 134 2Kb 132-136 CHALLA05- 146 2Kb 144-148 CHALLA05- 158 2Kb 156-160 CHALLA05- 170 2Kb 168-172 CHALLA05- 182 2Kb 180-184 CHALLA05- 194 2Kc 192-196 CHALLA05- 206 2Kc 204-208 CHALLA05- 218 2Kc 216-220 CHALLA05- 230 2Kc 228-232 CHALLA05- 242 2Kc 240-244 CHALLA05- 254 2Kc 252-256 CHALLA05- 266 2Kc 264-268 CHALLA05- 278 4PIb 276-280 CHALLA05- 290 4PIc 288-292 CHALLA05- 302 4PIc 300-304 CHALLA05- 314 4PIc 312-316 CHALLA05- 326 4PIc 324-328 CHALLA05- 338 4PIc 336-340 CHALLA05- 350 4PIc 348-352 CHALLA05- 362 2PIIa 360-364 CHALLA05- 374 2PIIa 372-376 CHALLA05- 386 2PIIa 384-388 CHALLA05- 398 2PIIa 396-400 CHALLA05- 410 4PIIa 408-412 CHALLA05- 422 4PIIa 420-424 CHALLA05- 434 4PIIa 432-436 CHALLA05- 446 4PIIa 444-448 CHALLA05- 458 4PIIa 456-460 CHALLA05- 470 4PIIa 468-472 CHALLA05- 482 4PIIa 480-484
CHALLA05- 518 4PIIb 516-520 CHALLA05- 530 4PIIb 528-532 CHALLA05- 542 4PIIb 540-544 CHALLA05- 554 4PIIb 552-556 CHALLA05- 566 4PIIb 564-568 CHALLA05- 578 4PIIb 576-580 CHALLA05- 590 4PIIc 588-592 CHALLA05- 602 4PIIc 600-604 CHALLA05- 614 4PIIc 612-616 CHALLA05- 638 4PIIc 636-640 CHALLA05- 650 4PIIc 648-652 CHALLA05- 662 4PIIc 660-664 CHALLA05- 674 4PIIc 672-676
CHALLA05- 722 3PIIIb 720-724 CHALLA05- 734 2PIIIa 732-736 CHALLA05- 746 4PIIIa 744-748 CHALLA05- 758 4PIIIa 756-760 CHALLA05- 770 4PIIIa 768-772 CHALLA05- 774 4PIIIa 772-776 CHALLA05- 782 4PIIIa 780-784 CHALLA05- 794 4PIIIa 792-796
CHALLA05- 806 2PIIIb 804-808 CHALLA05- 818 2PIIIb 816-820 CHALLA05- 830 2PIIIb 828-832 CHALLA05- 842 2PIIIb 840-844 CHALLA05- 854 4PIIIb 852-856 CHALLA05- 866 4PIIIb 864-868 CHALLA05- 878 4PIIIb 876-880 CHALLA05- 890 4PIIIb 888-892 CHALLA05- 902 4PIIIc 900-904 CHALLA05- 914 4PIIIc 912-916 CHALLA05- 926 4PIIIc 924-928 CHALLA05- 938 3PIVa 936-940 CHALLA05- 950 3PIVa 948-952 CHALLA05- 958 3PIVa 956-960 CHALLA05- 962 3PIVa 960-964 CHALLA05- 966 3PIVa 964-968 CHALLA05- 970 3PIVa 968-972 CHALLA05- 974 3PIVa 972-976 CHALLA05- 986 3PIVa 984-988 CHALLA05- 998 3PIVa 996-1000 CHALLA05- 1010 3PIVb 1008-1012 CHALLA05- 1022 3PIVb 1020-1024 CHALLA05- 1034 3PIVb 1032-1036 CHALLA05- 1046 3PIVb 1044-1048 CHALLA05- 1050 3PIVb 1048-1052 CHALLA05- 1058 3PIVb 1056-1060 CHALLA05- 1070 3PIVb 1068-1072 CHALLA05- 1074 3PIVb 1072-1076 CHALLA05- 1082 3PIVb 1080-1084 CHALLA05- 1094 3PIVb 1092-1096 CHALLA05- 1106 3PIVc 1104-1108 CHALLA05- 1118 4PIVa 1116-1120 CHALLA05- 1130 4PIVb 1128-1132 CHALLA05- 1142 4PIVb 1140-1144 CHALLA05- 1154 4PIVb 1152-1156 CHALLA05- 1166 4PIVb 1164-1168 CHALLA05- 1178 4PIVb 1176-1180 CHALLA05- 1190 4PIVb 1188-1192 CHALLA05- 1202 4PIVb 1200-1204 CHALLA05- 1214 4PIVb 1212-1216 CHALLA05- 1226 4PIVc 1224-1228 CHALLA05- 1238 4PIVc 1236-1240 CHALLA05- 1250 3PVa 1248-1252 CHALLA05- 1262 3PVa 1260-1264 CHALLA05- 1274 3PVa 1272-1276 CHALLA05- 1286 3PVa 1284-1288 CHALLA05- 1298 3PVa 1296-1300 CHALLA05- 1310 3PVa 1308-1312 CHALLA05- 1322 3PVa 1320-1324 CHALLA05- 1334 4PVa 1332-1336 CHALLA05- 1346 4PVa 1344-1348 CHALLA05- 1358 3PVb 1356-1360 CHALLA05- 1370 3PVb 1368-1372 CHALLA05- 1382 3PVb 1380-1384 CHALLA05- 1394 3PVb 1392-1396 CHALLA05- 1406 3PVb 1404-1408 CHALLA05- 1418 3PVb 1416-1420 CHALLA05- 1430 4PVb 1428-1432 CHALLA05- 1442 4PVb 1440-1444 CHALLA05- 1454 4PVb 1452-1456 CHALLA05- 1466 4PVb 1464-1468 CHALLA05- 1478 4PVb 1476-1480 CHALLA05- 1490 4PVb 1488-1492 CHALLA05- 1502 2PVIc 1500-1504
45
CHALLA05- 1514 2PVIc 1512-1516 CHALLA05- 1526 2PVIc 1524-1528 CHALLA05- 1538 2PVIc 1536-1540 CHALLA05- 1550 2PVIc 1548-1552 CHALLA05- 1562 3PVIa 1560-1564 CHALLA05- 1586 2PVIIa 1584-1588 CHALLA05- 1598 2PVIIa 1596-1600 CHALLA05- 1610 2PVIIa 1608-1612 CHALLA05- 1622 2PVIIa 1620-1624 CHALLA05- 1634 2PVIIa 1632-1636 CHALLA05- 1646 2PVIIa 1642-1646 CHALLA05- 1658 2PVIIa 1656-1660 CHALLA05- 1670 3PVIb 1668-1672 CHALLA05- 1682 2PVIIb 1680-1684 CHALLA05- 1694 2PVIIb 1692-1696 CHALLA05- 1706 2PVIIb 1704-1708 CHALLA05- 1718 3PVIc 1716-1720 CHALLA05- 1730 3PVIc 1728-1732 CHALLA05- 1742 4PVIb 1740-1744 CHALLA05- 1754 4PVIb 1752-1756 CHALLA05- 1766 4PVIb 1764-1768 CHALLA05- 1778 4PVIb 1776-1780 CHALLA05- 1790 3PVIIa 1788-1792 CHALLA05- 1802 3PVIIa 1800-1804 CHALLA05- 1814 3PVIIa 1812-1816 CHALLA05- 1826 3PVIIa 1824-1828 CHALLA05- 1838 3PVIIa 1836-1840 CHALLA05- 1850 3PVIIa 1848-1852 CHALLA05- 1862 3PVIIa 1860-1864 CHALLA05- 1874 3PVIIa 1872-1876 CHALLA05- 1886 3PVIIa 1884-1888 CHALLA05- 1898 4PVIIa 1896-1900
CHALLA05- 1910 4PVIIa 1908-1912
CHALLA05- 1934 4PVIIa 1932-1936 CHALLA05- 1946 4PVIIa 1944-1948 CHALLA05- 1958 4PVIIa 1956-1960 CHALLA05- 1970 4PVIIa 1968-1972 CHALLA05- 1982 4PVIIa 1980-1984 CHALLA05- 1994 4PVIIb 1992-1996 CHALLA05- 2006 4PVIIb 2004-2008 CHALLA05- 2014 4PVIIb 2012-2016 CHALLA05- 2018 4PVIIb 2016-2020
CHALLA05- 2054 4PVIIb 2052-2056 CHALLA05- 2066 2PVIIIc 2064-2068 CHALLA05- 2078 2PVIIIc 2076-2080 CHALLA05- 2090 2PVIIIc 2088-2092 CHALLA05- 2102 2PVIIIc 2100-2104 CHALLA05- 2114 4PVIIc 2112-2116 CHALLA05- 2126 4PVIIc 2124-2128 CHALLA05- 2138 4PVIIc 2136-2140 CHALLA05- 2150 4PVIIc 2148-2152 CHALLA05- 2162 4PVIIc 2160-2164