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Satellite tracking of flamingos in southern Africa: The importance of small wetlands for management and conservation

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The Makgadikgadi Salt Pans in Botswana are one of the most important breeding sites in southern Africa for lesser flamingos Phoeniconaias minor and greater flamingos Phoenicopterus ruber roseus. Much of flamingo migration behaviour is unknown and there has been speculation on the pattern of flamingo movements to and from Makgadikgadi and their dispersal throughout southern Africa. We carried out the first satellite tracking of flamingos in southern Africa to find out where lesser and greater flamingos go after leaving Makgadikgadi. In July 2001 five lesser and three greater flamingos were tagged. Following migration from the pans, one of the greater flamingos flew west to the coast of Namibia, the other south to a small wetland in South Africa. The lesser flamingos moved south-east from Makgadikgadi to South Africa and Mozambique. Movement by both species was nocturnal. This work shows that flamingos migrate from all over southern Africa to Makgadikgadi to breed. It also shows that, during the non-breeding season, movement is widely dispersed and nomadic among a network of wetlands around the subcontinent. Small wetlands, often unrecognized as important for conservation, provide valuable feeding sites and migration staging posts along flamingo migration routes. This highlights the need for the conservation of the network of small wetlands around southern Africa, which are often under threat from anthropogenic activities, to protect two high profile bird species in decline.
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Oryx Vol 37 No 4 October 2003
Short Communication
Satellite tracking of flamingos in southern Africa: the importance of
small wetlands for management and conservation
Graham McCulloch, Adrian Aebischer and Kenneth Irvine
Abstract The Makgadikgadi Salt Pans in Botswana are Africa to Makgadikgadi to breed. It also shows that, during
the non-breeding season, movement is widely dispersedone of the most important breeding sites in southern
Africa for lesser flamingos Phoeniconaias minor and and nomadic among a network of wetlands around
the subcontinent. Small wetlands, often unrecognized asgreater flamingos Phoenicopterus ruber roseus. Much of
flamingo migration behaviour is unknown and there has important for conservation, provide valuable feeding sites
and migration staging posts along flamingo migrationbeen speculation on the pattern of flamingo movements
to and from Makgadikgadi and their dispersal through- routes. This highlights the need for the conservation
of the network of small wetlands around southernout southern Africa. We carried out the first satellite
tracking of flamingos in southern Africa to find out Africa, which are often under threat from anthropogenic
activities, to protect two high profile bird species inwhere lesser and greater flamingos go after leaving
Makgadikgadi. In July 2001 five lesser and three greater decline.
flamingos were tagged. Following migration from the
pans, one of the greater flamingos flew west to the Keywords Flamingos, migration, Phoeniconaias,Phoeni-
copterus, satellite tracking, southern Africa, telemetry,coast of Namibia, the other south to a small wetland in
South Africa. The lesser flamingos moved south-east wetlands.
from Makgadikgadi to South Africa and Mozambique.
Movement by both species was nocturnal. This work This paper contains supplementary material that can
only be found online at http://journals.cambridge.orgshows that flamingos migrate from all over southern
Of the five species of flamingos that occur worldwide may have caused a >20% decline of flamingo numbers
over the last two decades. Collectively, small wetlandstwo, the greater flamingo Phoenicopterus ruber roseus and
the lesser flamingo Phoeniconaias minor, occur in Africa. also provide an important but poorly understood habitat
network for flamingos (Breen, 1991; Anderson, 2000c).The lesser flamingo is categorized on the IUCN Red List
as Lower Risk: near threatened across its entire range The conservation of flamingos on small ephemeral pans
and some perennial wetlands around southern Africa(Collar et al., 1994; IUCN, 2002) and both species are
listed in the African Eurasian Waterbird Agreement is of concern owing to the lack of formal, eCective pro-
tection of the majority of these increasingly threatened(AEWA, 2000) as ‘‘populations in decline throughout
southern Africa’’. Both species are considered Lower sites (Davies & Day, 1986; Allan, 1987; Breen, 1991;
Allan et al., 1995; Anderson, 2000c).Risk: near threatened or Vulnerable throughout southern
Africa owing primarily to the lack of breeding sites The salt pans of the Makgadikgadi depression are a
relict of an immense Quaternary palaeolake that onceand the vulnerability of breeding to both natural and
anthropogenic disturbance (Brook, 1984; Simmons, 1996; covered much of northern Botswana (Thomas & Shaw,
1991). The remnants of this great lake at Ntwetwe andAnderson, 2000a, b). Simmons (1996, 2000) has suggested
that a lack of successful breeding at the large wetland Sua Pans comprise a flat surface of saline clay that is
flooded intermittently with seasonal rainfall. Duringsites of Etosha Pan in Namibia and Sua Pan in Botswana
the rainy season (October–April), the pans are trans-
formed into vast shallow salt lakes that provide excellent
Graham McCulloch (Corresponding author) and
Kenneth Irvine Department of Zoology, Trinity College, feeding conditions for both species of flamingos. The
Dublin 2, Ireland. E-mail: mccullg@tcd.ie southern section of Sua Pan provides one of the most
important breeding sites for both species in southern
Adrian Aebischer, 2 Rte de Schiffenen 17, CH-1700 Fribourg,
Switzerland. Africa, with breeding success depending on the extent
of seasonal flooding (Hancock, 1990; Simmons, 1996).
Received 19 June 2002. Revision requested 25 September 2002.
Accepted 27 May 2003. The pans typically dry out at the end of each season,
480 © 2003 FFI, Oryx,37(4), 480–483 DOI: 10.1017/S0030605303000851 Printed in the United Kingdom
481
Satellite tracking of flamingos
often before breeding is complete, forcing the birds to oC, for 6 months, switching to a cycle of 8 hours on/
44 hours oC, for the time estimated to coincide with theseek food elsewhere (Hancock, 1990; Simmons, 1996).
Controversy surrounds the geographical origin of 6-month period around breeding and migration. The
PTT cycles were oCset from the 24-hour orbit cycles offlamingos that migrate to and from the pans, and while
evidence of movements to and from the direction of the receiving satellites to avoid possible transmission at
a time-window each day with few or no overpasses.Makgadikgadi are well documented (Borello et al., 1998;
Anderson, 2000c), details of their migration patterns and ‘On’ periods, therefore, occurred at diCerent times of the
day, alternating between nocturnal and diurnal trans-behaviour are unknown (Simmons, 1996, 2000; Borello
et al., 1998). It has been suggested, that because of missions. All data were transmitted through the Argos
satellite system. Location accuracy varied according tothe very high numbers, up to hundreds of thousands,
that occur on Makgadikgadi and Etosha in years of the PTT signal strength and the number of receiving
satellites (five in total ) during each transmission. Theexceptional rainfall (above the average of 400–500 mm)
these migrations may link with the East African popu- PTTs produced excellent data and we only used location
information with accuracies of 150–1,000 m of the reallation (Berry, 1972; Simmons, 1997; Borello et al., 1998).
In July 2001 we began the first satellite tracking of position. The locations of the all sites used by the tracked
flamingos are given in Fig. 1 and the Appendix.flamingos in southern Africa in an attempt to monitor their
movements from Makgadikgadi after an exceptional Owing to exceptional floods the pans did not dry up
in 2001 and the flamingos remained to complete anotherbreeding season. A total of 28 flamingos were caught
on Sua Pan using a noosing method similar to that used breeding season. Of the eight birds that were tagged,
PTTs on two greater and three lesser flamingo were stillin East Africa (B. Childress, pers. comm.) and South
America (B. Conway, pers. comm.). Using 80 and 30 g transmitting at roughly the same location, to the north-
east of Sua Pan (20°22S, 26°12E), when the pans finallyPTT satellite telemetry devices, we tagged five lesser
and three greater flamingos. The devices were attached began to dry out in February 2002. The greater flamingos
(GF a&GFb) left the pans between 18 and 20 Februaryusing a figure-of-eight style harnessing technique with
teflon ribbon (Nagendran et al., 1994). The transmission 2002 (Fig. 1). On 20 February GF ahad moved 170 km
west to a small pan on the western edge of thecycles of each device were set at 8 hours on/158 hours
15
20
20
25
30
25 30 35ºE
Etosha
Makgadikgadr
Botswana
Namibia
South Africa Lesotho
Swaziland
Mozambique
Zimbabwe
100km
GFb
GFa
LFa&b
GFc
(vi)
(v)(xiv)
(viii)
(xv)
(vii)
(xii)
(ii)
(i)
(x)
(ix)
(iii)
(iv)
(xiii)
(xi)
(xvi)
Fig. 1 The migration of two greater flamingos (GF a&b) and three lesser flamingos (LF a,b&c) from the Makgadikgadi salt pans to their
non-breeding destinations around southern Africa. Precise locations of all sites are given in the Appendix.
© 2003 FFI, Oryx,37(4), 480–483
482 G. McCulloch et al.
Makgadikgadi (site i). On 22 February it was located lands (sites xiv and xv) before returning once again to
Kamfers Dam in August. It remained there until the580 km south-east on a small lake (site ii), 5 km from
Springbok Pan in the western Gauteng Province of South PTT stopped transmitting in mid-September. On 10 May
LF bhad moved 200 km north-east, very close to wetlandAfrica. GF bleft Makgadikgadi on a westerly course
and during the night of 20 February was located 700 km site xv. The PTT stopped transmitting for a time on
29 June. It began transmitting again on 29 Septemberaway, flying in the direction of Etosha Pan (site iii), in
Bushmanland, north-eastern Namibia. Flamingos have and LF bhad then moved to Lake Nanghul (site xvi), a
perennial freshwater lake in southern Mozambique.been observed stopping at pans close to this location on
numerous occasions and were presumed to be transient Flamingo movement from Makgadikgadi was as a
result of the disappearance of water, forcing them toflocks, en route between Botswana and Namibia (Hines,
1993; Simmons et al., 1998). Part of this flight (54 km) leave. Thunderstorms may, however, be linked to their
arrival on the pans, as suggested by Simmons et al.was tracked continuously for 49 minutes with an esti-
mated average ground speed of 65 km hr1. At the time, (1998) (G. McCulloch, pers. obs.). The Tswana name for
flamingos in Botswana, meaning thunder and lightningEtosha Pan was dry and therefore unsuitable habitat for
flamingos. On 22 February GF bwas located on the bird, provides some support to this idea. Although none
of the tagged birds flew north-east, this study cannotcoast of Namibia, 45 km north of Walvis Bay, 1,230 km
from Makgadikgadi. On 26 February it had moved south discount the possibilities of migratory connections
with East African populations. Mozambique has beento Walvis Bay (site iv).
On 20 February all three lesser flamingos (LF a,b&c) suggested as part of a coastal route north for inter-
connecting populations (Borello et al., 1998). Inspectionwere still at Makgadikgadi. In the weeks following
their departure we observed a highly dispersed move- of the movement of birds suggests that some sites close
to Makgadikgadi (i, iii and ix) are transient points onment (Fig. 1). On 23 February LF aand bwere located
930 km south-south-east on Kamfers Dam (site v), an longer migration routes, as previously suggested (Hines,
1993; Simmons et al., 1998), while others are likely to beimportant non-breeding site in the Northern Cape
Province of South Africa. Regular observations of large important feeding sites for non-breeding populations.
The results, particularly those of LF a, also shownumbers of flamingos have been recorded on this wet-
land (Anderson, 2000c). On 26 and 28 February LF athat flamingos are highly scattered and movement is
nomadic among the many wetlands on which they havethen moved 130 km east, to Skoppan (site vi) and 60 km
north to a small pan (site vii) near Flamingo Pan. On been recorded (e.g. Borello et al., 1998; Anderson, 2000c).
The majority of sites chosen by the flamingos are located9 March it flew to another small wetland (site viii) 17km
south. LF cmade its first stop on a small pan (site ix) in areas where small, predominantly ephemeral, pans
and dams are concentrated (Seaman et al., 1991; Allan130 km south of Makgadikgadi, before flying to a wet-
land (site x) near Barbers Pan, where it was located on et al, 1995; Anderson, 2000c). Many small ephemeral
wetlands throughout southern Africa are, however,4 March. It was then located on the night of 6 March,
flying to a wetland in the Lake Chrissie area (site xi), vulnerable to disturbance and degradation from drain-
age, domestic waste and agricultural pollution (Davies160 km east. During this flight the bird flew 90 km in 90
minutes at an average ground speed of 60 km hr1. & Day, 1986; Allan, 1987; Breen, 1991; Allan et al 1995).
Furthermore, most wetlands, including coastal lagoonsDespite observations of flamingos occasionally flying
over land by day (e.g. Williams, 1993), we recorded such as Walvis Bay in Namibia, and many of the dams
and other man-made wetlands that often support largemigration in progress only during night-time ‘on’
periods, supporting the theory that flamingos in Africa flamingo populations, have no or limited protection
as conservation sites (Breen, 1991; Allan et al., 1995;fly between wetlands at night (Brown et al., 1982). Later
in the year some of the flamingos continued nomadic Anderson, 2000c). The vulnerability of sites that lack a
protected status (Ehrlich & Daily, 1993) is a great concernmovements to diCerent locations. GF amoved 40 km
south-south-west to a wetland (site xii) on 31 March, for flamingo conservation as, collectively, scattered and
small sites used by these birds are as equally importantwhere it remained until the PTT stopped transmitting
on 3 May. On 5 May GF bflew 45 km south to Sandwich in their life-cycle as are the larger sites that aCord
protection either because of their remoteness (e.g. SuaHarbour (site xiii ). It returned to Walvis Bay again on
2 June and later that month the bird was found dead Pan and Magkadikgadi) or legal status (e.g. Etosha Pan
and Kamfers Dam) or both. The results of this work(with the transmitter attached) on the edge of a salt
works pond 38 km north of Walvis Bay, where it was indicate the importance for flamingos of a network of
wetland sites across southern Africa and emphasizesreportedly scavanged by a jackal. On 21 April LF a
returned to Kamfers Dam (site v). In June and July it the need for a reappraisal of wetland protection in the
subcontinent.continued its nomadic movements, visiting small wet-
© 2003 FFI, Oryx,37(4), 480–483
483
Satellite tracking of flamingos
Davies, B.R. & Day, J.A. (1986) The Biology and Conservation of
Acknowledgements
South Africa’s Vanishing Waters. Centre for Extra-mural
Studies, University of Cape Town, Cape Town, South Africa.
We thank Disney Conservation Awards, Adelheid Ehrlich, P.R.D. & Daily, G.G. (1993) Population extinction and
Studer-Thiersch and Basel Zoo, PFG Glass (Pty) Ltd. saving biodiversity. Ambio, 22, 64–68.
South Africa, Bill Hunt and the International Flamingo Hancock, P. (1990) The flamingos of Sowa. Bushcall, 1, 16–21.
Foundation and Paul Henry and Botswana Ash (Pty) IUCN (2002) 2002 IUCN Red List of Threatened Species. IUCN,
Gland, Switzerland [http://www.redlist.org, accessed 9 July
Ltd. for financial support. We also thank Northstar and
2003].
Argos for the PTT transmitters and location information.
Hines, C.J.H. (1993) Temporary wetlands of Bushmanland and
Finally, a big thank you to Rob Simmons, Nicky Kavongo, northeast Namibia. Madoqua, 18, 57–69.
Bousfield, John and Pat Nurse and the Birdlife Botswana Nagendran, M., Higuchi, H. & Sorokin, A.G. (1994)
Club for their help catching and tagging the flamingos. A harnessing technique to deploy transmitters on cranes.
In The Future of Cranes and Wetlands. (eds H.M. Higuchi &
J. Minton), pp. 57–60. Wild Bird Society of Japan, Tokyo,
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... One critical knowledge gap and conservation priority is to identify wetlands used by Andean Flamingos throughout their full annual cycle, which has been identified as a priority for research (Caziani et al. 2007). Research on flamingos in Africa and Europe has shown that knowing which wetlands flamingos use at different times of year is critical to developing effective conservation measures (McCulloch et al. 2003, Amat et al. 2005. If flamingo movements are directional and predictable, a site-based conservation strategy (i.e., in which a handful of sites are targeted for conservation) is appropriate, whereas if their movements are highly variable, the best conservation approach may be one that focuses on protecting the species across its entire range (Roshier andReid 2003, Caziani et al. 2007). ...
... These sites were being used for foraging by flamingos, with no breeding activity observed, such that we do not know whether the flamingos we captured were breeding that season. Captures were carried out using leghold traps made of loops (17 kg test) of polyethylene fishing line positioned at 1 m intervals along a 100 m fishing line (34 kg test;McCulloch et al. 2003, Amat et al. 2005. Traps were placed underwater and held to the bottom of the lake by metal stakes in areas where Andean Flamingos were seen foraging. ...
... Andean Flamingo is included in Appendix I of the Convention on the Conservation of Migratory Species of Wild Animals, for which a memorandum was signed in 2008 by Bolivia, Chile, and Peru, but not Argentina. Such a disjointed international flamingo conservation effort, which has also been highlighted for Old World flamingos (e.g., McCulloch et al. 2003, Amat et al. 2005, is worrisome, given the fluid nature of the movements by Andean Flamingos that we detected between Argentina, Bolivia, and Chile (with one flamingo visiting all three countries). Additionally, Andean Flamingos use only a few breeding sites, with the Salar de Llullaillaco being one of only six known breeding sites in Argentina (Torres et al. 2019;E. ...
... A similar record was reported in Algerian semiarid saline wetlands (Sebkhat Ouled Amara and Ouled M'barek), in which the number of greater flamingos was higher in early winter (December) and lowest in mid-summer (August) (Bouaguel et al., 2013). The greater flamingos experienced a nomadic movement to different locations (McCulloch et al., 2003) and the considerable variations in the number of greater flamingos in the wetland seem to be a function of food availability (Battauz et al., 2013). In the current study, the wetland was dry from March to April and the birds abandoned the wetland. ...
... Examples of such areas include Melincué Lagoon in Argentina for Andean and Puna Flamingos, Lagoa do Peixe in Brazil for Chilean Flamingos, Kamfers Dam in South Africa for Greater Flamingo, and Indian wetlands for Greater and Lesser Flamingos, among others. These areas are often used as non-breeding areas, where the birds feed, forage, and rest before the breeding season, and are crucial for the social cohesion of the group and the re-establishment of optimal future flock reproductive conditions (McCulloch et al. 2003;Derlindati et al. 2014;Delfino and Carlos 2022). The disappearance and rapid unsuitability of these areas can have a high impact on these flamingos' populations, as it may also affect their breeding capacity, the health of adult individuals, and the overall fitness of the populations (Holyoak and Heath 2016). ...
... For example, in the Camargue hundreds of flamingos were observed taking off just before sunset to cover long distances during the night [36]. Such observation was also confirmed in African lesser flamingo (Phoeniconaias minor), which supports the theory that birds migrate between wetlands only at night [11,46]. Flying at night is believed to be energetically less costly because of a decrease in air turbulence and a reduction in evaporative water while taking advantage of the cooler and more humid nighttime air, thus reducing the chances of dehydration and overheating [10,39,40,59]. ...
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... Esto, junto con el valor más alto de especies por hectárea para la región, demuestran que este hábitat merece atención para su conservación, incluso por encima de áreas de mayor tamaño, tal como se ha hipotetizado para ecosistemas pequeños (Calhoun et al. 2017). Los estudios sobre lugares de descanso de aves migratorias y conjuntos de plantas raras muestran que los pequeños humedales son áreas críticas para la existencia continua de ambos grupos (McCulloch et al. 2003, Richardson et al. 2015, lo que aporta más evidencias sobre la necesidad de conservación de estos ecosistemas. ...
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The study of animal behaviour is important for the development of husbandry and management practices for zoo-housed species. Yet, data are typically only collected during daylight hours, aligning with human work schedules rather than animal activity patterns. To remedy this, 24 h data collection is needed. This study investigated the behaviour of a captive flock of lesser flamingos to understand temporal changes in their time-activity patterns. Two remote camera traps were placed around the birds' outdoor enclosure and one within the indoor house. Counts of birds visible within specific enclosure zones were recorded from photographic data. Behaviour was defined as active or inactive, and modified Spread of Participation Index (SPI) was used to calculate enclosure zone occupancy. Results indicated that lesser flamingos are active overnight, and to a similar amount as in the daytime. Proportions of birds observed as active were significantly higher at later times of the day (i.e., dusk) when compared to the number of active birds in the morning. Enclosure usage was diverse and indoor and outdoor zones could be used by different numbers of birds at different times of the day. Variation in enclosure usage may indicate the changing needs of the flamingos when housed indoors overnight and when they have night-time access to an outdoor enclosure. This research has identified the need for further research into the nocturnal behaviour and space use of lesser flamingos and suggests the need for 24 h research in captive birds, and other zoo-held species, especially when species are locked indoors or face behavioural restriction overnight due to biosecurity measures surrounding zoonoses outbreaks, e.g., Avian Influenza.
... We ultimately selected the fairly simple capture approach of submerged leg snares (hereafter, snares), which has been used successfully for other long-legged wading birds (Javed 2009;McCulloch et al. 2003). Not only are these snares easily transported, but they can also be constructed relatively quickly and inexpensively. ...
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We initiated a telemetry study on the Saddle-billed Stork (Ephippiorhynchus senegalensis) in western Zambia in 2019 to address knowledge gaps about spatial ecology. As the first such field study on the species, we encountered multiple challenges in attempting to capture free-ranging storks, including limitations in manpower and trapping techniques. In three field trips, we captured and deployed transmitters on only three storks. All transmitters have since failed, and the longest one transmitted data was for only five months, during which we recorded a dispersal event into Angola and back to its natal area. Our work has painstakingly demonstrated that field techniques are not always transferable between species and study systems, and that initiating work on an unstudied species has unforeseen difficulties.
... These pans have closed drainage and play a critical role in the hydrological cycle (Allan 1987). They are key habitats for biodiversity such as eubranchiopod crustaceans, migratory aquatic birds (McCulloch, Aebischer & Irvine 2003) and lifecycles stages of many invertebrate larvae (Nhiwatiwa et al. 2017). The biota have been documented to adopt one Ephemeral pans are transient natural habitats with harsh conditions found in semi-arid regions. ...
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Ephemeral pans are transient natural habitats with harsh conditions found in semi-arid regions. These pans endure high evaporation rates, extreme temperatures and an overflow of water. Pans are characterised by dry land becoming submerged in water temporarily (flood-like) followed by a prolonged period absent of water (drought-like). Ephemeral pans are unique habitats that are essentially transient habitats from a freshwater system to increased salinity and eventually a dry landscape. Biodiversity associated with these pans must adapt to the transient environmental conditions. Unique adaptations of the biota for these habitats allow them to withstand extreme conditions. The objective of this study was to (1) identify changes in the water quality over time in the pans, to (2) identify succession of macro-invertebrates and (3) identify the water quality parameters of pans as drivers of macro-invertebrate assemblages. A total of five pans were measured in the Northern Cape province of South Africa located on the Savanna and Nama-Karoo biomes within a 4500 ha area. The measurements taken included water quality variables (pH, salinity, total dissolved solids [TDS]), taxon diversity and richness of macro-invertebrates and aquatic birdlife. Evaporation rate between the pans varied with time. There was a difference in the macro-invertebrate taxon richness between the pans. Macro-invertebrate taxon succession was observed over time and some macro-invertebrates showed confinement to pans of a particular biome. It was found that pH was significantly the most contributing factor to the taxon richness and diversity of the macro-invertebrates recorded, while the salinity and TDS increased with time as water evaporated. Conservation implications: The shrimps (fairy, clam and tadpole) were unique to the Nama-Karoo pans. It was found that pH (p 0.05) was the most contributing factor to the taxon richness and diversity of the macro-invertebrates recorded, and salinity and TDS increased with time as water evaporated.
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An updated Atlas in the same general style as the book produced in 2002. Online version available at: www.atlasofnamibia.online
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Simmons, R.E., Barnard, P.E. & Jamieson, I.G. 1998. What precipitates influxes of wetland birds to ephemeral pans in arid landscapes? Observations from Namibia. Ostrich 70 (2): 145–148 The ability of wetland birds to rapidly find and exploit ephemeral pans is well known in and lands, but the episodic nature of such events means that the methods employed are poorly understood. Birds may: (i) wander randomly until wetlands are found; (ii) predict rainfronts and rainfall using changes in pressure gradients as cues; or (iii) follow rainfronts directly and descend onto pans as they fill. Observations from isolated pans in Namibia during the first rains indicate that wetland birds follow rainfronts, and descend onto pans as they fill. In one 30 ha pan, 37 birds of 5 species had arrived one day after filling and in another 50 ha pan over 300 birds of 13 species were attracted within 3 days of filling. Wetland birds, like migratory raptors, therefore, follow rainfronts, andMaywander locally thereafter. How species such as grebes and flamingos that exploit these pans for later breeding and intercontinental movements (respectively) time their flights to coincide with fully flooded pans remains unknown.
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Habitat rehabilitation or intervention to prevent species declines are rarely employed in Africa. I argue that despite protection in national parks, active intervention is necessary to halt declines in southern Africa's Greater (Phoenicopterus ruber) and Lesser (Phoeniconaias minor) Flamingo populations. Flamingos are long-lived species that breed sporadically at only two localities in southern Africa: the Makgadikgadi Pans in Botswana and Etosha National Park in Namibia. Despite well-publicized breeding on Etosha Pan, flamingos have experienced only three major breeding events in 40 years. Breeding failure occurs when high evaporation rates rapidly dry the pan, and up to 100,000 flightless chicks may starve. Consequently, pairs breeding in Etosha exhibit extraordinarily low recruitment (0.040 young pair/year) and extrapolations indicate that adults can replace themselves only if they breed for 38 to 50 years and all offspring survive. Because survival of offspring from fledging to adulthood (5 years) is about 46%, this breeding lifespan rises to an unrealistic 83 years, making Etosha a nonviable breeding site. Alternative, suitable flamingo habitats in Africa are being mined for soda-ash, are damaged by pollution, or are unprotected. Accordingly, continent-wide estimates and those from southern Africa alone suggest a population decline of about 40% in both species over the last 15 years. Because Namibia regularly supports 84% of the Greater and 93% of the Lesser Flamingos in southern Africa, conservation strategies are best focused there. Simple but effective management methods, based on those employed in western Europe, could reverse these downward trends. In Etosha a small island surrounded by a water-filled depression would allow up to 4000 pairs to breed annually. The benefits of enhancing the breeding of flamingos in Etosha include research opportunities, tourism revenue, and a safe haven for two Red Data species.
Article
Inland salt lakes are widely distributed in southern Africa: they are particularly common in South Africa, but many occur in Namibia and Botswana. All are shallow, and most are ephemeral with salinities that are not very high (mostly < 50 g l−1). Fringing zones of halophytes or submerged macrophytes are neither well-developed nor taxonomically diverse. The Cyanobacteria, especially Nodularia spumigena, often dominate the phytoplankton. The fauna of the Makgadikgadi area (northeast Botswana) is diverse and is similar to that of East African salt lakes. The aquatic fauna of salt water south of the Makgadikgadi Basin, on the other hand, is extremely depauperate, has no well-defined assemblage confined to saline waters, and appears mostly to comprise tolerant freshwater forms. Lovenula falcifera and Metadiaptomus transvaalensis (diaptomid copepods), Moina micrura (Cladocera) and Brachionus plicatilis (Rotifera) are frequently encountered zooplankton species, a few species of insects (Anisops sp., beetles, chironomids and ephydrids) are the principal non-planktonic macroinvertebrates. Artemia ‘salina’ is occasionally present, but may be an introduced form. The avifauna, in contrast to the aquatic macroinvertebrate fauna, is rich, with the greater and lesser flamingo often common.
The conservation status of the pans in the Lake Chrissie area
  • D G Allan
Allan, D.G. (1987) The conservation status of the pans in the Lake Chrissie area. In Proceedings of a Symposium on the Ecology and Conservation of Wetlands in South Africa (eds R.D. Walmsley & M.L. Botten), pp. 91–100. Report Series No. 28, Ecosystem Programmes, Foundation for Research Development, CSIR, Pretoria, South Africa
The Biology and Conservation of Acknowledgements South Africa's Vanishing Waters. Centre for Extra-mural Studies
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Davies, B.R. & Day, J.A. (1986) The Biology and Conservation of Acknowledgements South Africa's Vanishing Waters. Centre for Extra-mural Studies, University of Cape Town, Cape Town, South Africa.
Declines and movements of Lesser Africa Department of flamingos in Africa
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endorheic pans of South Africa. In Wetlands of South Simmons, R.E. (2000) Declines and movements of Lesser Africa (ed. G.I. Cowan), pp. 75–101. Department of flamingos in Africa. In Conservation Biology of Flamingos Environmental ACairs and Tourism, Pretoria, South Africa. (eds G.A. Baldassarre, F. Arengo & K.L. Bildstein), pp. 83–84.
Club for their help catching and tagging the flamingos. A harnessing technique to deploy transmitters on cranes
  • John Bousfield
  • Pat Nurse
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Bousfield, John and Pat Nurse and the Birdlife Botswana Nagendran, M., Higuchi, H. & Sorokin, A.G. (1994) Club for their help catching and tagging the flamingos. A harnessing technique to deploy transmitters on cranes. In The Future of Cranes and Wetlands. (eds H.M. Higuchi & J. Minton), pp. 57–60. Wild Bird Society of Japan, Tokyo, References Japan.
Temporary wetlands of Bushmanland and Finally, a big thank you to Rob Simmons
  • C J H Hines
Hines, C.J.H. (1993) Temporary wetlands of Bushmanland and Finally, a big thank you to Rob Simmons, Nicky Kavongo, northeast Namibia. Madoqua, 18, 57–69.