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On the relative role of climate change and management
in the current desert locust outbreak in East Africa
Christine Meynard, Michel Lecoq, Marie-pierre Chapuis, Cyril Piou
To cite this version:
Christine Meynard, Michel Lecoq, Marie-pierre Chapuis, Cyril Piou. On the relative role of climate
change and management in the current desert locust outbreak in East Africa. Global Change Biology,
Wiley, In press, pp.1-3. �10.1111/gcb.15137�. �hal-02747701�
Glob Change Biol. 2020;00:1–3. wileyonlinelibrary.com/journal/gcb © 2020 John Wiley & Sons Ltd
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1 Received: 9 April 2020|
Revised: 21 April 2020|
Accepted: 21 April 2020DOI: 10.1111/gcb.15137
L E T T E R T O T H E E D I T O R
On the relative role of climate change and management in the
current desert locust outbreak in East Africa
The current outbreak of the desert locust has affected much of eastern Africa and has reached as far as Pakistan and India in Asia, generating significant agricultural losses in a region that is already highly unstable economically, politically and in terms of food secu-rity for its human populations (FAO, 2020).
Desert locust outbreaks require a combination of weather, soil and vegetation conditions that favour the reproduction and aggregation of otherwise solitary individuals (Despland, Collett, & Simpson, 2000; Figure 1a). When those conditions appear, locusts aggregate, multiply in large numbers and migrate long distances, turning into a plague and devastating crops on their way. Solitary populations, which act as reservoirs for the gregarious forms, are likely to shrink their distribution under climate change because of a decrease in moisture and increased temperatures in much of the current recession range (Meynard et al., 2017). However, climate change could also expand part of this range at the margins, which includes some of the historical outbreak areas (Figure 1a; Meynard et al., 2017). Most importantly, outbreaks can start in very limited areas, from where swarms can travel thousands of kilometres. Therefore, a general shrinkage of the recession range does not nec-essarily translate into a decrease in the risk of outbreaks and plagues. As the waxing and waning of the monsoon rules the North African weather, rainfall, a major contributor to outbreaks, is erratic and difficult to forecast. Climate change scenarios include intensifi-cation of extreme weather events that could favour swarm forma-tion in some outbreak areas. For example, in spite of a significant long-term trend of increased incidence of drought in Africa (Thomas & Nigam, 2018), formation of swarms in 2018 was favoured by heavy rains caused by two tropical cyclones in the Arabian Peninsula. These extreme weather events allowed three generations of des-ert locusts to develop and go undetected until they spilled over into a much wider region (FAO, 2020). For these weather conditions to translate into agricultural risk, rainfall must be combined with fa-vourable vegetation and soil conditions, which may themselves re-sult from an interaction between climate and vegetation but also relates to human-induced change in land use (e.g. agriculture, wood extraction, urbanization), for which we do not have reliable fore-casts. Mechanistic models, which include the transition from soli-tary to gregarious forms in interaction with climate, vegetation and soil, are therefore urgently needed to accurately project the risk for desert locust outbreaks under climate change scenarios.
Beyond global change drivers, it is important to remember the long record of desert locust outbreaks, along with their management
success during the second half of the last century (Sword, Lecoq, & Simpson, 2010). Weather conditions that favour the development of swarms have been a constant threat to agriculture in the region for millennia (Waloff, 1966), and the climatic events observed since 2018 fall within the historical range (Abram et al., 2020). During the 20th century, research and international cooperation resulted, under the aegis of the Food and Agriculture Organization (Lecoq, 2003), in a concerted management effort based on identifying local hotspots where favourable conditions occur (e.g. Piou et al., 2019), to control potential swarm formation before they transform into a large-scale unmanageable threat (Figure 1a). This approach resulted in a consid-erable decrease in the number and intensity of locust outbreaks and plagues (Figure 1b). A key condition to the success of this manage-ment strategy, however, is the on-the-ground work that needs to be done in a sustained manner: active monitoring, information sharing between countries, preparation of the logistics for efficient control, maintenance of expertise over time, availability of emergency funds and crisis management plans. Detecting and controlling early stages of the swarm formation is therefore the most important step in this otherwise successful preventive strategy (Magor, Ceccato, Dobson, Pender, & Ritchie, 2005).
So, why did this particular outbreak wreak havoc and affect such a large area? We believe the answer lies mostly in socio-political instability. Since 2015, various countries in the Middle East and eastern Africa have been involved in armed conflicts or suffered from permanent insecurity. Some of the countries involved were therefore unable to sustain an expertise and monitoring effort that is perceived as only sporadically needed (Gay, Lecoq, & Piou, 2018). The early stages of swarm formation therefore went unchecked until the swarms had already turned into a plague (FAO, 2019).
The conditions that allowed this outbreak to expand as a plague and acquire such dangerous proportions can be compared to the cur-rent COVID-19 pandemic crisis. These have a synergistic effect with growing human densities and climate change effects on productive systems and human health. They both require a concerted moni-toring and on-the-ground control effort across borders, along with resources, expertise and infrastructure to support those actions. Moreover, these efforts must be kept in place over the long term to build resilience, despite the apparent lack of imminent threats (Gay et al., 2018). The lack of such a coordinated and sustained effort is likely to put human populations in many developing nations at dangerously higher risk. However, this also gives us hope in that the scientific knowledge that is required to manage those outbreaks at
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LETTER TO THE EDITORthe onset has already shown its worth. Reinforcing early detection systems to prevent large-scale outbreaks is made even more critical by climate change, which may lead to more common propitious con-ditions in some of the outbreak areas. Our highest priorities should therefore be (a) to ensure that the political and socio-economic con-ditions are in place so that vulnerable human populations can adapt to new large-scale threats and (b) to maintain a culture of long-term risk assessment with constant necessary means.
Christine N. Meynard1
Michel Lecoq1,2
Marie-Pierre Chapuis1,2
Cyril Piou1,2
1CBGP, Univ Montpellier, CIRAD, INRAE, Institut Agro, IRD,
Montpellier, France
2CIRAD, UMR CBGP, Montpellier, France
Correspondence
Christine N. Meynard, CBGP, 755 Avenue du Campus Agropolis, CS 30016, 34988 Montferrier-sur-Lez cedex, France.
Email: christine.meynard@inrae.fr
F I G U R E 1 Possible states of desert locust populations with their transition drivers and distribution (a) and the historical occurrence
of plagues and recession periods (b). (a) Grey rectangles indicate management actions at each state; blue text indicates conditions for the transition from one state to the next. Global change, including land use and climate change, is most likely to affect conditions that promote the transition from solitary to gregarious populations (1)→(2). For example, although climate change scenarios point to an increase in aridity and further desertification in vast areas of Africa, some regions that have been at the origin of past outbreaks are likely to see a reversed trend (i.e. increase in frequency and intensity of rains). Vegetation is likely to respond to these changes, although the interaction between climate change, soil conditions, vegetation and human-driven land use change might be complex. Further studies are needed to anticipate the potential result of these interactions with respect to desert locust outbreak risk in the future. (b) Recent history of the desert locust situation (updated from Sword et al. (2010) with the most recent data from FAO until March 2020). The figure shows the number of countries reporting swarms for the period 1910–2020. Between 1910 and 1963, there was an onset or full plague event in 41 out of 53 years, whereas between 1964 and 2020 there have only been 8 years (out of 56 years) with smaller plague events. In 2019, and up to 1 April 2020, there were 15 and 18 countries, respectively, that had reported swarms
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3 LETTER TO THE EDITORORCID
Christine N. Meynard https://orcid.org/0000-0002-5983-6289
Michel Lecoq https://orcid.org/0000-0003-4515-3505
Marie-Pierre Chapuis https://orcid.org/0000-0003-4405-7722
Cyril Piou https://orcid.org/0000-0002-9378-9404
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