Falko T. Buschke’s research while affiliated with KU Leuven and other places

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Publications (68)


Fig. 1. (A) Schematic drawing of an inselberg, showing the rock outcrop, the surrounding fringe of vegetation and the landscape matrix in which it is embedded. (B) Overview of common shapes of inselbergs s.l. (C) Examples of unique microhabitats associated with inselbergs.
Fig. 3. Examples of different rock outcrops that can be considered inselbergs (s.l.) based on the definition proposed in this review. (A) Large monolithic granite inselberg south of Harare, Zimbabwe, with vegetation on the summit. (B) Sugarloaf Mountain, another granite dome in Rio de Janeiro, Brazil. (C) A flat table-shaped sandstone mesa in the Free State, South Africa. (D) A low granite shield inselberg with temporary rock pools in Comoé National Park, Ivory Coast. (E) Herðubreið, a volcanic tuya from Iceland. (F) Fenglin tower karst in Guizhou China. Photograph credits: A and D, B. Vanschoenwinkel; B, L.F. de Paula; C, F.T. Buschke; E, J. Kluftinger; F, Pixabay.
Fig. 5. (A) Inselbergs in dryland and desert environments often have a fringe of vegetation around their base that is much denser than that of the landscape matrix, benefiting from local moisture and nutrient concentrations. (B) Inselbergs in moist (sub)tropical environments typically have xeric microhabitats on their summit or in the shallow soils near their base (C) The combination of these two situations can result in a spatial extension of the ranges of certain taxa beyond their typical biomes increasing regional biodiversity.
Fig. 7. Potential mechanisms of how inselbergs can act as refugia (A, B) and species pumps (C) in landscapes. (A) Species ranges contract to inselbergs during cycles of climatic change and recolonise the matrix afterwards. (B) The species' phenotype changes during its time on the inselberg via local adaptation or drift, and a different phenotype recolonises the matrix. (C) Different phenotypes evolve on different inselbergs which may increase diversity in the matrix when they manage to colonise it.
Fig. 8. (A) Graphical illustration of how the dispersal ability and general mobility of organisms may determine how they experience an inselberg landscape. Three contrasting situations are shown: inselberg specialists with poor dispersal ability perceive inselbergs as true islands; better dispersers may perceive inselbergs as patches in a metapopulation; while highly mobile organisms may perceive inselbergs as features in the landscape they use during their daily activities. (B) Relevant theories and processes associated with each situation.
The ecological and evolutionary dynamics of inselbergs
  • Article
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October 2024

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914 Reads

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1 Citation

Biological reviews of the Cambridge Philosophical Society

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Islands are fundamental model systems in ecology, biogeography, and evolutionary biology. However, terrestrial islands, unlike their aquatic counterparts, have received comparatively less attention. Among these land islands, inselbergs (i.e. isolated rock outcrops with diverse lithologies and a modest topographical prominence) stand out as iconic examples distributed worldwide across global biomes. Due to their durable lithology, inselbergs change slowly, persisting for tens of millions of years. In this review, we propose a biological definition for inselbergs that captures three fundamental characteristics of inselbergs from the perspective of biota. These are old age, isolation and the presence of unique microhabitats that are rare or absent in the surrounding matrix, fostering distinct communities often with unique and endemic biota. We synthesise the state of the art and formulate a set of testable hypotheses to deepen our understanding of the origins and maintenance of diversity on inselbergs, which are increasingly exposed to anthropogenic threats. By offering different habitats compared to the surrounding habitat matrix (e.g. moist microhabitats in dryland landscapes and xeric environments in humid tropical landscapes), insel-bergs may allow specific lineages to thrive beyond their typical geographical limits. Particularly in drylands and degraded landscapes, inselbergs may not just provide different habitats but also act as ecological refuges or evolutionary refugia by providing a wider range of potential microhabitats than the surrounding matrix, enhancing resilience and promoting regional biodiversity. The central role of the matrix ensures that the ecological and evolutionary dynamics of inselbergs differ from those of true islands such as oceanic islands. Given that inselberg biota coexist within a terrestrial matrix, interactions between inselberg and matrix populations impact each other significantly. Over evolutionary timescales, matrix species may contract to inselberg refugia, preserving lineages while cycles of isolation and reconnection may drive speciation via a species pump. Although inselberg biodiversity has been studied predominantly from an island biogeography perspective, we argue that depending on the spatial scale, habitat specificity and mobility of the organisms considered, a range of different theories and paradigms can help explain the biogeography and local distribution patterns of different taxonomic and functional groups of inselberg species.

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A bioassay of mine-affected soils and ameliorants in semi-arid rehabilitation

December 2023

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30 Reads

South African Journal of Plant and Soil

Global restoration is a priority given the onset of the United Nations’ decade for restoration. It is challenging to restore arid lands from mining impacts, especially where topsoil deficits exist. Successful rehabilitation is essential for alternative land use after mining. This bioassay aimed to establish whether and why some combinations of iron ore mine-affected soils and ameliorants are more effective in promoting plant growth than others. We examined the responses of one thousand radishes (Raphanus sativus)to five mine-affected soils and four soil ameliorations (soil improvement using fertiliser and organic matter) over two different seasons (early and late rainy seasons). We found that soil characteristics affected plant production regardless of amelioration and that some soil/amelioration combinations were significantly better than others. Topsoil ameliorated by moderate fertiliser application produced the best results. Waste rock could support germination and plant production when ameliorated with certain organic compost and fertiliser combinations. Untreated mine-affected soils had low to no plant production. Plant responses to the different soil/amelioration combinations were affected by season. Our findings suggest that area-specific bioassay investigations and their results could improve management decisions to achieve rehabilitation targets for mine-affected soils.



Figure 1: The geographic location of local and sub-national case studies valuing ecosystem services 134 across Eastern and Southern Africa from the Ecosystem Services Valuation Database (Brander et al., 135 2023). Points are coloured according to the type of ecosystem service and scaled according to the 136 standardised economic value (International $.ha -1 .year -1 for the year 2020). Shaded areas denote 137 protected areas from the World Database for Protected Areas (UNEP-WCMC and IUCN, 2022). The 138 two Indian Ocean island states of Mauritius and Seychelles are not displayed on this map because 139 there were no local or sub-national ecosystem service valuation case studies for either country. 140 141
Figure 2: The standardised value (International $.ha -1 .year -1 ) of different types of ecosystem services 241 in protected and unprotected areas. Grey points show empirical values from 561 case studies. Coloured 242 squares show predictions from a log-linked Gamma generalised linear mixed effects models with six 243 countries included as random factors. The horizontal axis is log-scaled. 244 245
The values of ecosystem services inside and outside of protected areas in Eastern and Southern Africa

September 2023

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241 Reads

Conservation policies often take for granted the importance of protected areas for supplying ecosystem services. The 1st edition of the State of Protected and Conserved Areas in Eastern and Southern Africa report contained limited information on ecosystem services, so for the upcoming 2nd edition we compared statistically 561 standardised economic values of various types of ecosystem services inside and outside of protected areas. We found that data from local and sub-national case-studies in the Ecosystem Service Valuation Database were biased geographically, highlighting major evidence gaps for most of the region. For well-studied countries (Botswana, Ethiopia, Kenya, South Africa, Tanzania, Uganda), the value of ecosystem services varied considerably across different types of services but were - on average - five times higher outside protected areas. This trend was not universal, however, given that opportunities for recreation and tourism tended to be 20 times higher within protected areas. Combined, these findings suggest that conservation authorities across Eastern and Southern Africa (1) prioritise ecosystem service valuation studies; (2) expand the focus of ecosystem service policies to include wider landscapes beyond protected area boundaries; and (3) avoid making generic assumptions about ecosystem services by identifying which types of services are most compatible with the broader goals of protection.





Fig. 4.1 Geographical distribution of biodiversity features in the six local municipalities of Thabo Mofutsanyana District Municipality. a The position of Thabo Mofutsanyana District in South Africa, and b the elevation and location of the six local municipalities. c Critical Biodiversity Areas (CBA) and Ecological Support Areas (ESA), d Key Biodiversity Areas (KBA), e Existing protected areas and protected area focus areas, and f Strategic Water Sources Areas (SWSA) for surface and ground water
Fig. 4.3 The geographic characteristics of spatial biodiversity plans of six local municipalities within Thabo Mofutsanyana District Municipality. a The surface area of each local municipality in hectares. b The median elevation across municipalities, with minimum and maximum elevation as error bars. c The percentage coverage of features from the map of Critical Biodiversity Areas, which includes two levels of Critical Biodiversity Areas (CBA 1 & 2) and Ecological Support Areas (ESA 1 & 2). d The percentage coverage of Key Biodiversity Areas. e The percentage coverage of protected areas and focus areas earmarked for protected area expansion. f The percentage coverage of Strategic Water Sources Areas for ground and surface water
Using Local Spatial Biodiversity Plans to Meet the Sustainable Development Goals

January 2023

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1 Citation

The Sustainable Development Goals (SDGs) represent global development ambitions, but achieving these goals depends on local-level application. Many local governments, especially in countries with emerging economies, lack the capacity and resources to integrate SDGs into municipal planning. The feasibility of local implementation is particularly challenging in areas with rugged topography and international borders, such as the Thabo Mofutsanyana District Municipality, South Africa, into which the city of Phuthaditjhaba falls. Here we explore the suitability of existing spatial biodiversity plans for local application in the six local municipalities within Thabo Mofutsanyana District. We considered four plans related to biodiversity and ecosystem services, including international maps of (1) Key Biodiversity Areas and (2) Strategic Water Source Areas; a national (3) Protected Area Expansion Strategy; and a provincial map of (4) Critical Biodiversity Areas. Although these plans were not designed specifically to meet the SDGs, we show that they can be repurposed to address seven of the 17 SDGs. Next, we summarised the spatial coverage of each plan across the six local municipalities and evaluated the opportunities and shortcomings of using these plans for local application. Our findings guide local officials on the most efficient way to plan for the SDGs using currently available spatial products.


Coal and Water: Exploiting One Precious Natural Resource at the Expense of Another?

September 2022

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1 Citation

Coal is an important energy resource in South Africa. The environmental sustainability of coal extraction is however questionable. This is especially true for natural water sources, which can be severely degraded by coal mining activities. The impacts of coal mining on water resources include direct, indirect, induced, and cumulative impacts. In this chapter, the authors assess the total impact of coal mining pollution on water bodies in Emalahleni within the eMalahleni-Witbank coalfield of the Mpumalanga Highveld. The effects of land use around Emalahleni on the ecosystem’s natural water purification function were simulated. The simulation allowed the authors to quantify the cumulative impacts of changing rainfall patterns anticipated under climate change, as well as some scenarios of continued ecosystem degradation or restoration. Induced impacts on municipal water supply have also been assessed by summarising water usage data from an Emalahleni household survey. The case study offers a comprehensive overview of the challenges facing the water-energy nexus and demonstrates how integrating the water and energy sectors is essential for securing a more sustainable future.


Citations (43)


... The introduction of exotic species and the resulting extinction of local species can have profound environmental, economic, and social consequences (Johnson et al., 2020), and these impacts are also evident in the unique biota of inselbergs (Porembski 2000;Porembski et al. 2016). Given the ecological significance of inselbergs (Vanschoenwinkel et al. 2024) and their vulnerability to invasive species (de Paula et al. 2015), it is crucial to identify and assess the invasive potential of these exotic species. This study presents the first comprehensive list of exotic species specifically compiled for inselbergs in the Atlantic Forest and Caatinga-two phytogeographical domains in Brazil recognized for their exceptional biodiversity and high concentration of granite outcrops. ...

Reference:

Exotic plant species on inselbergs of Brazilian tropical forests: insights for biodiversity management and conservation
The ecological and evolutionary dynamics of inselbergs

Biological reviews of the Cambridge Philosophical Society

... Finally, the LPI has benefitted from long-term institutional support from the current partners WWF UK and the Zoological Society of London, which is one of the key factors identified for indicator uptake by the Biodiversity Indicators Partnership [26]. That the LPI's development is overseen by these NGOs based in Europe, and not by an IGO, could be a barrier to national uptake, particularly as data ownership can be a critical factor in how biodiversity information is used [93]. Some agreements such as the SDGs require their indicators to have a recognized custodian agency such as a UN body. ...

Make global biodiversity information useful to national decision-makers

Nature Ecology & Evolution

... However, one methodological factor may cause these time series to bias the LPI towards overall decrease. Population dynamics are affected by variability arising from demographic, environmental, and sampling stochasticity, which introduces uncertainty into the LPI 15,20 . To mitigate this uncertainty, a smoothing procedure based on the GAM method is applied during the index calculation. ...

Reply to: Capturing stochasticity properly is key to understanding the nuances of the Living Planet Index

Nature Ecology & Evolution

... The level of dependence is more extreme in the province's Emalahleni municipality which produces 50% of SA's energy and hosts 60-70% of the country's 80,000 coal miners . Most of the power stations were constructed between the 1960-1980's and have high levels of water use, while air pollution has turned the region into a pollution hot spot (Esterhuyse and Buschke, 2022). ...

Coal and Water: Exploiting One Precious Natural Resource at the Expense of Another?
  • Citing Chapter
  • September 2022

... For instance, dental mesowear analysis of Pleistocene (~1 Ma to 600 ka) herbivores from Elandsfontein indicates that many presumed grazers (e.g., alcelaphin antelopes) consumed more dicots than suggested by their craniodental morphology or by their extant relatives (Stynder, 2009). Likewise, we have previously noted that isotopic analyses of fossil herbivores from several Pleistocene localities in the interior of South Africa-where most grasses follow the C 4 photosynthetic pathway-frequently indicate an important C 3 dietary component in grazer lineages (e.g., equids and alcelaphins) (e.g., Codron et al., 2008Codron et al., , 2023Codron et al., , 2024Ecker et al., 2018b;Lee-Thorp and Beaumont, 1995). Though this may be indicative of C 3 grass consumption (Ecker et al., 2018a;Lee-Thorp and Beaumont, 1995), it is also possible that Pleistocene 'grazers' in southern Africa consumed more dicots than their present-day counterparts. ...

Competition drives the evolution of emergent neutrality in the dietary niches of mammalian herbivores
  • Citing Article
  • November 2021

Quaternary International

... Aggregation of population trends from multiple species can give rise to misleading overall trends due to random population fluctuations (Buschke 2021). The overall population trend from aggregate indices can mask a combination of increasing and declining populations (Buschke 2021). ...

Neutral theory reveals the challenge of bending the curve for the post‐2020 Global Biodiversity Framework

... The largely arid southern African region is consequently considered an important biodiversity hotspot for large branchiopods (Brendonck & Williams, 2000;Nhiwatiwa et al., 2014;Brendonck et al., 2022). Although arid areas, like the western half of southern Africa, support a proportionally large number of temporary wetlands (Goudie & Wells, 1995;Brendonck & Williams, 2000;Brendonck & Riddoch, 1997), most of the collecting and research has largely been on the mesic, subtropical eastern half (Hamer & Appleton, 1996a;Hamer & Martens, 1998;Ferreira et al., 2011Ferreira et al., , 2012Nhiwatiwa et al., 2014;Mabidi et al., 2016;Dube et al., 2020;Pinceel et al. 2021) and in fynbos vegetation (de Roeck et al., 2007;Mlambo et al., 2011). Anostracans, which comprise by far the most diverse taxon of Branchiopoda in southern Africa with 46 species at that time (currently 51), was demonstrated to have a high correlation between diversity and rainfall gradient, as coastal and subtropical areas exhibited highest diversity (Hamer & Brendonck, 1997). ...

Co‐occurrence of large branchiopods and killifish in African savannah ponds

... Fairy shrimp populations from inselberg rock pools rely on partial hatching of a reserve of dormant resting eggs to survive dry periods. This prevents population extinction during inundations that are too short for maturation and reproduction and was shown to represent an evolutionary bet-hedging strategy (Pinceel et al., 2021). Mobile animals may simply leave when conditions are unfavourable and return afterwards. ...

An empirical confirmation of diversified bet hedging as a survival strategy in unpredictably varying environments

... Some technical limitations are common to multi-species indices, such as the sensitivity of the geometric mean to outliers [20], zero values [81,82] and rare species [82,83]. Furthermore, uncertainty from both measurement of the population and stochasticity within a population tends to bias a geometric mean downwards [81,84], and this is especially pronounced when population trends covary [85]. Other sensitivities detected in the LPI relate to the unevenness in temporal coverage found within the dataset, where short or sparse time series tend towards declining trends but also demonstrate higher uncertainty in the trend estimates [81,86]. ...

Random population fluctuations bias the Living Planet Index

Nature Ecology & Evolution

... One theme throughout the present study was the emphasis on the importance of co-design, co-development and collaboration from users and developers in the Global South and the recognition of the risks of excluding communities (Jarvis et al. 2020). Similar to other studies focused on single tools or disproportionately representing different user groups (Davies et al. 2009, Jepson & Ladle 2015, Finer et al. 2018, Musinsky et al. 2018, Weisse et al. 2019, Shea 2022, our study documented the many tools that can be exclusionary in both big and small ways, ranging from infrastructure inequities preventing access, to insufficient resources or a lack of authority to act, to simple design flaws. ...

Navigating spaces between conservation research and practice: Are we making progress?