Managing drought and locust invasions in Africa
Thomas R. Odhiambo
The two most critical African natural disasters - drought and
locust outbreaks - are least understood in terms of the four activities
considered essential to long-term disaster reduction: hazard prediction, risk
assessment, disaster preparedness, and disaster management. In finding a
solution to the drought and desertification that plague Africas
Sudano-Sahelian belt, planners would do well to study indigenous adaptations to
the unpredictable Sahelian ecosystem. They should study them, translate them
into scientific terms, validate them, and try to implement them to stabilize the
Sahelian and other drought-prone ecosystems. The key to solving the problem of
locust swarms may lie in the work being done by the International Centre of
Insect Physiology and Ecology. ICIPE hopes by studying the behavior of locusts
to find a way to dampen the locusts swarming cycle and intensify their
solitary cycle so that locust populations can maintain a relatively sedentary,
grasshopper-like lifestyle. ICIPE hopes that solitary locusts can continue to
exist as natural herbivores in Africas semiarid breeding grounds,
continuing their participation in the dynamics of the savannah ecosystem without
periodically breaking into locust plagues.
A.J.W. Taylor (1978) described disasters as catastrophic
events that (a) interfere with everyday life, disrupt communities, and often
cause extensive loss of life and property, (b) overtax local resources, and (c)
create problems that continue for longer than those that arise from the normal
vicissitudes of life. In this sense, disasters need not be sudden,
unexpected, or devastating. Otherwise, disasters such as drought, famine, and
epidemics would be excluded. All disasters - industrial or natural - vary in the
degree of vulnerability to which victims are subjected and the special attention
they require. But disasters caused by the forces of nature are perhaps the
most readily accepted, even if with despair and resignation. They represent the
unleashed fury of the natural world against which mankind is quite
helpless (Taylor 1978). This feeling of helplessness has given new impetus
to a search for long-range solutions to the management of two pervasive natural
disasters in Africa: drought and locusts.
The true dimensions of poverty are existential rather than
economic, wrote Albert Tevoedjre (1978). To Walter Weisskopf (1989),
misery reflected impotence:
The medieval world outlook believes in a
supernatural, but comprehensible order. The Newtonian model believed in an order
routed in nature and comprehensible through reason. Having abandoned a belief in
providence, grace and other worldly rewards for religions virtue as well
as the deterministic belief in nature and reason, the Heisenbergian paradigm
seems to deprive us of all protection against the threat of the unknowable
future and of the unknowable reality. (Quoted in Giarini and Stahel
1989.)
The point about such impotence is that peoples
traditional, communal ability to cope with recurring setbacks can no longer
provide a safety net for victims. They have become more vulnerable, and natural
disasters have become an ultimate crisis of destitution. Consequently, more than
any other community, Africas scientific community today has the
responsibility of creating a new perception of natural disasters.
Developing long-range solutions to the two most difficult
natural disasters in Africa - drought and locust outbreaks - requires an
information-intensive, management-aware strategy. In 1988, the UN
Secretary-General appointed an international ad hoc group of experts to
recommend a scientific framework for launching the International Decade for
Natural Disaster Reduction (IDNDR) for the 1990s. That group considered four
kinds of activity essential to a solution-oriented long-range program:
· Hazard
prediction through monitoring, early warning systems, and the like.
· Risk assessment - for
example, by mapping hazard levels.
· Disaster preparedness,
especially by training key personnel, educating the general public, and
appropriately controlling land use and construction.
· Disaster management, by
developing schemes for local evacuation, establishing lines of emergency supply,
and mobilizing civil defense groups.
Drought and locust outbreaks are poorly understood in terms of
these four activities. As the group of experts stated in its report:
Drought is a complex environmental phenomenon,
including long-term climatological changes and wide-scale ocean/atmosphere
interactions as well as ecological deterioration of human origin. The management
of drought as a natural disaster has many factors in common with management of
disasters of more sudden onset. Drought predisposes the environment to several
rapid-onset natural hazards, including locust infestations and, in many
instances, flash floods. Drought alone causes large agro-ecological damage and
seriously disrupts socioeconomic life. Over this century, droughts have tended
to intensify as a result of accelerating deforestation and large-scale soil
erosion, especially in Africa; their management globally has become a matter of
urgent action.
These catastrophic phenomena now demand a thoroughgoing
scientific explanation, leading to solution-oriented technologies that may well
incorporate elements of social invention. What Africa needs is to master science
and technology, not merely identify with it. This requires that problem-solving
become the principal aim of our scientific endeavor focused on drought and
locusts. We must become dissatisfied with the existing state of knowledge about
these natural processes and events, mistrusting the obvious and searching for
the underlying order in natural processes (Sindermann 1985).
Drought in Africa
The Food and Agriculture Organization (FAO) of the United
Nations predicts that unless Africa takes corrective action, rainfed croplands
on the continent will become 30 percent less productive by the end of the 1990s,
mostly because of soil depletion and erosion (World Resources Institute 1989).
Part of Africas unrealizable potential for agricultural productivity is
the 40 percent of the continent that is either extremely arid or subject to
cyclical drought.
The Sahara, the largest desert in the world, receives less than
100 millimeters of precipitation a year (Conservation for Development Centre of
IUCN 1986). Other arid areas, such as the Kalahari Desert in the south, also
suffer chronic low precipitation, usually with high temperatures. Drought, on
the other hand, is a temporary feature, experienced only when rainfall deviates
appreciably from normal levels (of about 200 millimeters a year). Drought can
occur in virtually any rainfall or temperature regime (Lockwood 1988). The Sahel
- the zone across the continent south of the Sahara Desert, with annual rainfall
of 200 millimeters - has experienced a north-south migration in its 600,000
years of human occupation. The Sahel has now stabilized between 13 degrees north
and 19 degrees north, but the research of A.M. Lezine and her colleagues shows
that the zone has shifted substantially in the past 20,000 years, a period that
has been studied in some detail. Rock paintings show a succession of scenes from
game-rich savannah to cattle-herding pastoralists to desert panoramas.
Geomorphological and palaeontological evidence in the guise of fossil river
systems and drainage networks (for instance, the Wadi Howar system in the Sudan)
contains fossil remains of crocodiles, hippos, and river bivalves - in a region
that now receives merely 25 millimeters of precipitation a year. Pollen analyses
indicate that fossil lakes in the Sahel (for example, the Selima Oasis) once
sustained savannah grasslands in areas now hyperarid. These studies conjure an
image, some 18,000 years ago, of savannah grassland with scattered acacia trees
that extended only as far north as 10 degrees north, which is further south than
its current geographical limit. In 8500 before the present (BP),
moisture-demanding types of vegetation extended northward rapidly, eventually
reaching 400-500 kilometers north of their current agro-ecological limit.
Reversal of this northward shift began in about 6100 BP and intensified in about
4500 BP; Sahelian vegetation as we know it today became established in its
present zonal limits (13 degrees north and 19 degrees north) about 2,000 years
ago.
Despite this volume of evidence, and the more recent episodes of
drought in the Sahel during this century - including the great drought of 1984
that caused about 100,000 deaths - we cannot yet predict drought (Conservation
for Development Centre of IUCN 1986). We believe that arid lands are rapidly
spreading in Africa, often aided by the long cyclical drought periods, based on
observations on the fringes of the Sahel and similar semiarid and arid areas
such as the Kalahari and Namib Deserts, Somalia, and North Eastern Kenya (UNEP
1985). This aridification, and the rapid deforestation of much of Africa, is
leading to three critical phenomena:
·
Desertification of the Sahel, through bushfires, overgrazing, increased
harvesting of fuelwood, and the spread of cultivation to marginal lands.
· Sahelization of the
savannah grasslands.
· Savannahization of the
forests.
Desertification has now reached 88 percent in Sudano-Sahelian
Africa, 80 percent in southern Africa, and 83 percent in Mediterranean Africa.
We cannot yet accurately quantify in time and space the changes associated with
desertification, sahelization, and savannahization. Nor are we certain about the
factors that determine the onset of drought, although some associations are
becoming apparent.
Past studies suggest that drought in Africa south of the Sahara
is correlated with (1) drought in the Central America-Caribbean Atlantic region
and (2) warm sea-surface temperatures and rainfall on the Pacific coast of Latin
America (associated with the so-called El Niffect) - in other words,
associating African drought with interactions between the ocean and the
atmosphere (Rind and others 1989). Similarly, rainfall in the western Sahel is
affected by anomalies in sea-surface temperatures in both the Pacific and Indian
oceans. Not that these examples reflect a direct causal relationship. Rather,
the droughts over much of the Sahel and North Africa are associated with the
reduced (but not delayed) northward extension of the Inter-Tropical Convergence
Zone (ITCZ), the band of wet weather that circles the world at the point where
the trade winds blowing from the Northern and Southern Hemispheres meet (Rind
and others 1989).
For all our ignorance of what causes cyclical drought in Africa,
its impact on the human population is profound. The two-decade drought from
1966-67 to 1987 was the worst for 150 years but others almost as bad have
occurred every 20 to 25 years or so. Under these circumstances, it is
meaningless to speak of protecting the environment. Rather, a way should be
found to fit human activities into the reality of the natural systems.
Of the worlds 40 million nomadic pastoralists - whose
livestock-based economies survive on deserts or semiarid savannahs - 25 million
live in Africa, most now relegated to marginal lands (Bass 1990).
Anthropological studies reveal that traditional pastoralists knowledge of
the environment in which they live and work is highly complex and organized -
their plant and animal breeding and husbandry the result of experiential
fact-finding that cannot be ignored by modem scientists. According to a Dutch
study, quoted by the Independent Commission on International Humanitarian Issues
(1985), traditional herders produce as much protein per hectare as do
ranches in areas of equal rainfall in the United States and Australia; the
Sahelian herders, however, accomplish this with infinitely less mechanical
energy inputs, relying for the most part on manpower. This husbandry,
based on traditional knowledge, requires that the Sahelian herder not stay in
one place - lest overgrazing and desertification set in. Settling herders in
semiarid areas is therefore often unwise:
Sedentarizing nomads ignores the fact that they
employ their marginal resources better than anyone else could. Nomads have lower
birthrates than their settled neighbors. Their family herds support more people
on the land than do commercial ranches. Nomads make few demands on the state,
and they practice the kind of self-sufficiency that any enlightened government
should want to encourage (Bass 1990).
Indigenous Sahelian social systems were intimately linked to
their agro-ecosystems, until externally imposed changes in recent times led to
environmentally destructive change, such as the charcoal production associated
with trans-Saharan trade and the expansion of transportation networks (Gritzner
1988). Indigenous adaptations to the unpredictable Sahelian ecosystem -
including integrated agro-sylvo-pastoral practices - are not only highly
sophisticated but have inherent scientific validity (Gritzner 1988). We would do
well to understand them, translate them into scientific terms, validate them,
and then try to implement them to stabilize the Sahelian (and other
drought-prone) ecosystems.
Desert locust swarms
The Sahel is full of other surprises. One recurrent problem is
occasional massive outbreaks of locust swarms. In October 1988, desert locusts
(Schistocerca gregaria) bred on an unprecedented scale along much of the
Sahel, so that in early October several swarms of them reached the Atlantic
coast of West Africa - from Guinea-Bissau in the south to Mauritania in the
north - then invaded the Cape Verde Islands on October 5-6 and 12. Soon
thereafter, the locusts were sighted over the Atlantic Ocean and began reaching
the eastern West Indies from October 14, stretching from St. Croix in the north
to the coastal areas of Guyana and Suriname in the south. They made this
intrepid landfall 4,500 kilometers from the West African mainland with the
assistance of the tropical storm Joan (Rainey 1989).
There are at least five important locust species (and their
ecogeographical subspecies) in Africa: the desert locust, the tropical migratory
locust (Locusta migratoria migratorioides) found everywhere in Africa and
beyond, the red locust (Nomadacris septemfasciata) found in
Eastern-Central Africa, the brown locust (Locustana pardalina) found in
Southern-Central Africa, and the Senegalese grasshopper (Oedaleus
senegalensis) in West Africa and the Atlantic Ocean islands. Undoubtedly,
the desert locust is the most intractable, widespread, and perennially
destructive of all these pestiferous locusts. There are at least 200 other
grasshopper species resident in the Sahel that live normally as herbivores in
this savannah ecosystem without swarming as marauding migrants.
In normal years - during the frequent drier periods when the
desert locust goes into recession - the species is widely distributed over a
wide belt of arid and semiarid lands (including the African Sahel), covering
some 16 million square kilometers. Under this recession, the desert locusts live
as inconspicuous, solitary grassland herbivores in these semiarid areas. Major
locust swarms develop as a result of a rapid increase in locust numbers among
the erstwhile recession population when widespread, heavy, prolonged rains occur
after a long stretch of drought, in several scattered breeding areas. These wet
periods permit two or three generations of the locust to develop in each
breeding area, multiplying rapidly - sometimes by a factor of 105.
These aggregate, match as hoppers, then swarm as adults, becoming highly mobile
and traveling up to 1,000 kilometers a week, assisted by winds. Such gregarious
locust swarms arise only after favorable rains, occurring over several seasons,
succeed a long stretch of drought years (COPR 1982). The locusts may well invade
a much larger area, covering some 29 million square kilometers, taking in all of
the Sahel, North Africa, the Mediterranean region, the Middle East, and West
Asia.
The old hypothesis that locusts migrate from areas that have
become untenable is not correct. The flying locust swarms tend to be carried
toward areas where rain has fallen, following the Inter-Tropical Convergence
Zone (COPR 1982). The late Reginald Rainey (1989), who made a life-long study of
locust migration, concluded, after 40 years studying locust swarming phenomena,
that migration is intrinsically adaptive - that locusts use migration as a
mechanism to exploit seasonal changes in the spatial distribution of
environmental resources. The desert locust simply exploits the necessary
environmental resources by becoming airborne, and latching onto the
geographically patterned global and local wind systems, which eventually take
them to their convergence zones and their rains. The locusts then exploit the
ephemeral vegetation, which develops quickly after unusually good rains over an
area normally occupied by arid thornbush. This larger invasion area is often
even more fragile than the locusts usual recession breeding area, so the
locust invasion wreaks devastation.
The change from inconspicuous, solitary, grasshopper-like
individuals (in the drought years) to highly mobile, gregarious, marauding
locust swarms (early in the wet years) is associated with a major change in
locust behavior, and fairly accurate forecasting systems exist for the
appearance of matching hopper bands and locust swarms. The onset of recession -
the petering out of locust plagues - is not so simple to predict. We have few
clues as to what causes this behavioral change. In 1965-66, desert locust
infestations worldwide were at their lowest level in 27 years, and an equally
significant 18 years of locust silence followed. Rainey thought that the decline
of desert locust infestations in the mid-1960s was associated with a
marked change in the global wind circulation, which had reverted sharply to a
type of regime which had prevailed before the 1890s when desert locust
swarms had also been rare. The hypothesis is that these prolonged locust
recessions are associated with a shift of the desert zones toward the equator,
with equatorial rains (and the ITCZ) more concentrated than before close to the
equator (Rainey 1989). It is recognized that these changes do not necessarily
entail a direct causal relationship.
The challenge of managing locust invasions
It is a major challenge for the world scientific community -
particularly Africans, who have lived with periodic marauding locust swarms for
at least 600,000 years, since humans first settled in the Sahel - to begin to
manage this natural disaster effectively. It is the belief of the International
Centre of Insect Physiology and Ecology (ICIPE) that long-range desert locust
management technologies will arise only when scientists know the behavior of
locusts intimately and can interrupt mechanisms that regulate such
behavior.
Attempts to change the physiology and behavior of the locust
between the solitary and gregarious phases are at the heart of ICIPEs
innovative attempts to ground the locust - to make it remain sedentary,
behaving as a solitary, grasshopper-like population - and to keep it
permanently nonswarming, nonmigratory, and nonmarauding. These efforts, never
before tried, are one approach to sustainable management of the desert locust.
Other approaches include use of the locusts natural enemies (including
parasitoids and pathogens), the selective use of chemical locusticides, and a
more refined locust forecasting and monitoring system. It is ICIPEs
conviction that interrupting the gregarization, the sexual maturation, and the
oviposition pheromone systems (which together bring about the rapid and
synchronized development of coherent, highly dense locust swarms), together with
promoting the solitarization and sexual maturation-inhibition pheromone system
(which intensify solitarization), should help locust populations maintain a
relatively steady sedentary, grasshopper-like lifestyle. By accomplishing this
goal, ICIPE hopes it will help the pheromone-maintained solitary locusts
continue to exist as natural herbivores in Africas semiarid breeding
grounds, continuing their important role as a participant in the dynamics of the
savannah ecosystems, without periodically breaking out into locust
plagues.