Yield losses caused by FAW in selected countries in sub-Saharan Africa
The fall armyworm (Spodoptera frugiperda J.E Smith) (Lepidoptera: Noctuidae) invaded Africa in 2016, and has since spread to all countries in sub-Saharan Africa, causing devastating effects on mainly maize and sorghum. The rapid spread of this pest is aided by its high reproductive rate, high migration ability, wide host range and adaptability to different environments, among others. Since its introduction, many governments purchased and distributed pesticides for emergency control, with minimal regard to their efficacy. In this chapter, we review efforts towards managing this pest, highlight key challenges, and provide our thoughts on considerations for sustainable management of the pest.
- Spodoptera frugiperda
- Zea mays
The fall armyworm (FAW)
2. Origin and distribution
The FAW is native to the tropical and sub-tropical regions of the Americas . It was first described in 1797 in the state of Georgia, USA. It remained a pest in the Americas until 2016 when it was first reported in West Africa (Nigeria), and the island of São Tomé and Principe , and subsequently in almost all sub-Saharan African countries within one year [6, 7, 8, 9, 10, 11]. To date, it is known to occur in five continents (Africa, Asia, Australia, North and South America). The FAW possesses a great potential to cover wide geographical locations in a short period . The rapid spread of the pest is attributed to its high reproductive capacity, high migration ability and a wide host range.
3. Biology of the fall armyworm
The FAW undergoes complete metamorphosis (egg, larva, pupa and adult) (Figure 1). Under optimal conditions, the development of FAW takes approximately 30 days. The eggs are laid on leaves in batches containing 100–200 eggs . Each female can lay an average of 1500 eggs, with a maximum of over 2,000 eggs in a life time  . Eggs hatch in two to three days during summer . There are six larval instars with a development duration of two to three weeks, with the last instar being most destructive (causing 70% of FAW damage) . The FAW generally pupates in the soil at a depth of 2 to 8 cm in a cocoon constructed by tying together particles of soil with silk . The pupal stage lasts about eight to nine days during summers . Adults are nocturnal, and most active during warm, humid evenings. The adults live for about, but lifespan ranges between 7 to 21 days .
Presently, there are two major strains of FAW known in both the native and invasive range [16, 17]. These are the ‘corn’ (C strain) and the ‘rice’ (R strain) strains, which are defined by the host where they develop. The corn strain attacks corn/maize, sorghum and cottons, while the rice strain attacks grasses, like rice, silk grass and some forage grasses. The two strains are morphologically identical but differ in genetics, physiology and behavioral characteristics, such as mating and resistance to insecticides . Both strains are present on the African continent . In addition to these strains, there exist mutant strains with resistance to different insecticide classes in both the Americas [19, 20, 21] and Africa [22, 23].
4. Host plants, damage and losses caused in maize
The FAW is a polyphagous pest reported to feed on at least 353 crop and non-crop species from 76 plant families , with a high preference for the Gramineae family . Farmed grasses like maize, rice, sugarcane, and sorghum are recorded as major hosts whereas dicotyledonous vegetables and cotton are documented as minor hosts . The number of hosts is likely to increase as this pest expands into newer areas [27, 28, 29]. Although it is polyphagous, FAW prefers to feed on maize causing substantial yield loss in SSA .
The larvae damage plant leaves, stems, branches, and reproductive organs, such as flowers and fruits. The damage by first instar larvae on grasses such as maize appear as silvery patches called the “windowpanes” because one side of the leaf is eaten, leaving the opposite epidermal layer intact. Damage by the third and fourth instar larvae is more pronounced with holes appearing on the edges going inwards and the characteristic row of perforations due to feeding on the whorl of the growing plants are visible. The larvae also migrate from the leaves to the tassels and the developing ears/grains leading to grain yield losses and exposing the grains to mycotoxin contamination (Figure 2). Commonly observed in maize is reduced plant stand in young crops and defoliation of older plants .
The losses associated with FAW vary with factors such as host species, varieties, environmental conditions, and socio-economic factors. In maize, FAW infestation starts from the seedling stage till the reproductive stages (Figure 2), causing quantitative and qualitative grain losses. The qualitative losses involve contamination with aflatoxins and fumonisins . In Africa, maize losses were estimated to be 8.3 to 20.6 million tons, causing annual losses of US$2,481–6,187 million . Yield losses is selected African countries are shown in Table 1.
Beside the direct effects on yields, FAW infestation may result in significant expenditures on insecticides for both the farmers and governments, and detrimental effects of residual chemicals on human health and the environment [4, 32]. The reduced yields may affect other value chain actors such as livestock farmers who may suffer reduced quantities and quality of maize stover, maize-based food processors who may suffer reduced volumes leading to reduced trade.
5. FAW surveillance, monitoring and field assessments
Surveillance at the farm level is an informal and passive way of detecting pest problems as they emerge . Monitoring on the other hand is an exercise that actively tracks the presence and movement of a pest within a given area  and is often organized and implemented at various scales, mostly by governments, through trained technical personnel who collect data according to prescribed sampling protocols. Data collected is used to make decision on management of the pest.
In 2019, FAO and CABI advocated for FAW monitoring using commercial pheromone lures and traps to give advance warning to farmers at the beginning of the maize cropping season. To promote harmonization of data collection and reporting procedures as well as foster collaboration among regional member countries, FAO developed a Fall Armyworm Monitoring and Early Warning System (FAMEWS) mobile application tool which requires users to input both field scouting and pheromone trap data . The application tool also helps farmers to correctly identify FAW while providing them with off-line, free control advice delivered via satellites .
In addition to FAMEWS, FAO and Pennsylvania State University jointly developed and launched an innovative talking mobile app called
Monitoring of adult FAW using sex pheromone traps (attractive to male moths) is informative of the presence of the pest within a location. Experiments conducted in French Guiana  showed that FAW pheromone trap data can be used to estimate, a week in advance, the subsequent abundance of larvae in pastures. However, the above prediction method has been found to be unreliable in crops. For example, McGrath et  observed no relationship between the number of FAW male moths caught in traps and the number of female moths laying eggs in the same locality. The foregoing can be attributed to FAW’s pre-oviposition period of 3–4 days and migratory tendencies, which therefore means that populations of egg-laying moths in an area may be dominated by migrants which previously mated elsewhere. Thus, catches of male moths in traps should simply be used to estimate the presence of potential egg-laying females in the area.
FAW’s lack of diapause combined with a conducive climate in most countries of SSA obviously mean that there are always some populations which do not undertake long-distance migrations as they simply shift to off-season irrigated maize. In the context of managing resistance at a national or regional level, surveillance and monitoring programs can be very useful in mapping the dispersal of insecticide resistant FAW populations. Using an appropriate mark-recapture approach as that used by Osborne et al. (e.g., , it should be possible to identify the invasion zones of an insecticide-resistant FAW population arising from a known area. Guidelines on what pesticides to use or not to use in these invasion zones can be issued to curtail the further buildup of selection pressure for resistance development.
Four most used parameters in a FAW field assessments include:  pest incidence (% field infestation),  plant damage (based on a visual scoring system),  pest density per plant or field and  yield. For scoring of damage, the Davis and Williams  0–9 visual rating scale is the most commonly used in sub-Saharan Africa [38, 39, 40]. However, other researchers have collected FAW damage data using modified versions of the above visual scale. For example, Caniço et al.  from Mozambique assessed plant damage in the field using a scale of 0–5, where 0 equals plants with no visual foliar damage, and 5 plants with more than 75% foliar damage or dead from FAW. For evaluating the effectiveness of Bt maize and insecticides for FAW control in Brazil, Burtlet et al.  collected damage data based on a visual scale  and converted the scales to percentage damages. Maize yield losses due to FAW attack have also been estimated using a variety of protocols, for example the digital imaging method . Rodriguez-del-Bosque et al.  compared the weights of damaged kernels per cob with the weight of the same number of undamaged kernels . Based on these few examples, standardization of data collection and analysis protocols is needed to enable comparison of results across regions and countries.
6. Management of the FAW
The methods advocated for controlling the FAW in Africa are agroecological/cultural, biological control, host plant resistance, transgenic approaches and chemical pesticide use . Below is a review of the use of the above methods on the continent.
6.1 Agroecological management
Agroecological management is the science of applying ecological principles to enhance productivity while reducing the negative impacts on the environment [45, 46]. Successful agroecological management is based on the understanding of key principles such as complex interactions within the ecosystem and contextualized solutions to local problems . Agroecological management practices to reduce FAW populations in Africa include cultural and mechanical control, intercropping, crop rotation with non-host crop, weed management and intercropping maize with the moth repellant Greenleaf desmodium (“Push”) with
6.1.1 Cultural and mechanical control of FAW
Cultural control methods for FAW include removal of crop residues and no-tillage. A significant reduction of FAW infestation on maize was observed in maize farms under minimum or no-tillage in Zimbabwe . Minimum tillage also enhances activities of natural enemies. Among the mechanical control methods recommended for and used smallholder farmers in Africa is squashing egg masses and hand-picking small larvae [4, 50, 51]. Farmers in different parts of Africa also resorted to applying sand, ash, or soil in the maize whorl [43, 51, 52]. However ash, soil, and alata samina soap (made from the ash of the barks of plants that are locally harvested, such as plantain, palm tree leaves, and shea tree bark)  treatments were found not to be effective in reducing FAW larvae numbers or crop damage at the dosages tested, and thus did not significantly increase maize yields .
6.1.2 Weed manipulation
There are mixed observations about the influence of weeds on the population and damage by FAW. For example, Altieri  observed significantly less infestation of maize due to FAW in weedy (natural weed complex or selected weed associations) plots compared to weeded plots. Furthermore, in the weedy farm of maize, significantly greater number of FAW predators were encountered. On the contrary, in Zambia, the incidence of FAW was low in frequently weeded plots that were dominated by graminaceous spp. . Bearing in mind the crop-weed competition effect, allowing weeds other than graminaceous in between maize rows and as guard rows enhances the population of natural enemies . Despite the beneficial effect of weeds on the population of arthropod pests, their infestation could cause about 20–50% yield losses in maize . Thus, striking a balance in keeping and removing weeds is important in ensuring high farm productivity.
Intercropping (Figure 3) practiced widely by smallholder farmers in sub-Saharan Africa has long been recognized as an efficient farming system providing improved resource utilization and increased productivity [57, 58]. The practice is reported to reduce pest populations and enhance the potential of their natural enemies [59, 60]. In Latin America, maize-bean intercrops reportedly reduced FAW infestation when compared to a maize monocrop . Similarly, studies in Uganda and Cameroon have demonstrated that intercropping maize with beans or groundnuts significantly reduces FAW infestation and damage severity in maize (Figure 3) [41, 44]. In Cameroon, a maize intercrop with climbing beans resulted in higher reduction of FAW numbers, compared to bush beans . In the above studies, the yield of maize in the intercrop increased by almost two-fold, compared to the monocrop. However, the effect of intercropping on grain yield was not comparable to that of synthetic pesticides where a three-fold yield increment was observed. Although further studies are required to determine the mechanism by which intercropping reduces damage caused by the FAW, barrier effect, repellant volatiles emission and enhanced natural enemy abundances are speculated to be key mechanisms .
6.1.4 Planting dates of maize in intercrops and monocrops
Early planting of companion crops in a maize cropping system seems to provide masking effect resulting in reduced FAW infestation. For example, a study where simultaneous planting of maize with beans and sequential planting where maize was planted after 20 to 30 days resulted in a significantly less FAW infestation compared to simultaneous cropping . Similar observation was made in maize under push-pull technology where the perennial desmodium sprouted prior to the maize germination. It is however observed that sole maize planted early equally suffers less damage compared to late-planted maize (Otim, pers. Obsv).
6.1.5 Conservation agriculture
The basic principles around conservation agriculture include minimum tillage, crop rotation, and cover crop or mulching . In no-tillage plots where crop residue from the previous harvest was applied as mulch, oviposition and damage by FAW was significantly lower in maize at 2 to 3 leaf stage compared to the plowed plots . The masking effect of the mulch helps maize to escape the early infestation of FAW. Although the level of infestation was less, the effect of the mulch was at par with the plowed farm 20 days after planting, implying the masking effect. Findings from Zambia showed significantly less FAW infestation in maize under zero tillage followed by minimum tillage .
6.1.6 Push-pull technology
A novel agricultural technology based on cereal/legume intercropping was developed to tackle multiple problems including insect pests and weeds while augmenting soils with nutrients. The technology was developed by the International Center of Insect Physiology and Ecology (
In a study conducted by Midega et al.  in Kenya, Uganda, and Tanzania, the team reported 82.7% and 86.7% reduction in larvae per plant and plant damage, respectively in climate-adapted push-pull compared to maize monocrop plots, and a resultant 2.7-fold higher grain yield in the climate-adapted push-pull plots (Figure 6). There was a similar finding in Uganda, where maize yield from climate-adapted PPT was significantly greater compared with maize intercropped with edible legumes or mono-cropped maize .
6.2 Biological control of FAW in Africa
Centuries of research on FAW in the Americas have recognized the importance of biological control in the management of FAW in its native range. Biological control does not only offer a sustainable solution to FAW management, but also presents an economically and environmentally safer alternative or complement to synthetic pesticides as well as a vital solution for mitigating potential pesticide resistance that is often associated with inappropriate pesticide use . The key categories of natural enemies of FAW are predators, parasitoids, entomopathogens (fungi, bacteria, viruses and nematodes). In Africa, efforts are underway to identify the natural enemies of FAW, assess their impacts and harness their use in the overall management of the pest.
6.2.1 Natural enemies of FAW reported in Africa
Studies on the identification of natural enemies of the FAW in Africa have been reported from different countries including Benin, Cameroon, Cote d’Ivoire, Ethiopia, Ghana, Kenya, Mali, Mozambique, Niger, South Africa, Tanzania, and Uganda. Most of the natural enemies of FAW reported since the advent of the pest on the continent are parasitoids. These are mainly Dipterans and Hymenopterans and were found on either egg, larvae, or pupae of the pest. Highest diversity was found among larval parasitoids, and included
Few studies have paid attention to predatory species on FAW in Africa. Koffi et al.  recorded
Since FAW was reported in Africa, limited research reports exist on entomopathogens of FAW. Akutse et al.  demonstrated ovicidal and larvicidal potency of isolates from
6.3 Use of botanical against fall armyworm in Africa
In Ethiopia, Sisay et al.  associated more than 90% larval mortality to botanical insecticides, namely
The ever-increasing diversity of natural enemies being reported across the continent calls for an intensification in the search for local natural enemies coupled with their conservation and mass rearing for conservative and augmentative biological control programs. Priority should be given to this approach over classical biological control and more efforts are required across the continent for prospection for natural enemies, rearing, performance assessment, mass production and release. Efficacy trials are being conducted in various countries for botanicals and biopesticides. Critical aspect hindering their adoption might be the comparatively higher costs compared to chemical pesticides. Thus, strong advocacy activities are required to engage policy makers in establishing conducive environment for wider use of biological control products over chemical pesticides.
6.4 Host plant resistance for managing fall armyworm
Host plant resistance (HPR) is a cornerstone for any pest management strategy. The use of insect-resistant crop varieties as a component of IPM arises from the ecological compatibility and compatibility with other direct control tactics . HPR works in synergy with biological, cultural, chemical and agroecological practices and works with synergy . HPR is very specific to the target pest or group of pests and does not affect the non-target organisms. HPR is also very persistent throughout the cropping season. The quantitative or polygenic nature of native genetic resistance also offers the opportunity to minimize selection pressure on FAW and prevents emergence of new resistant strains. Moreover, HPR does not involve any additional cost to the farming community the farmers do not need any training and the scaling up with be easily adopted in the farming community in Africa.
The FAW, an invasive pest which recently invaded Africa has evolved with wild maize and later with domesticated maize in Latin America. It is expected therefore that these constant interactions resulted in some degree of genetic adaptation. The genetic resistance to FAW in some plants including maize was available since 1990’s . The United States Department of Agriculture (USDA) Agricultural Research Service (USDA-ARS, Mississippi) developed and released a series of maize inbred lines with resistance to FAW including Mp496, Mp701–708, Mp713, Mp714, and Mp716 [81, 84, 85, 86, 87, 88, 89], derived primarily from germplasm held by the International Maize and Wheat Improvement Center (CIMMYT, Mexico). CIMMYT developed populations from tropical and subtropical maize inbred lines, CML59–74 and CML121–127, from USDA-ARS germplasm, with FAW resistance .
Since the invasion of FAW in Africa, intensive and precise screening of maize germplasm against FAW under artificial infestation by CIMMYT has been ongoing in Kiboko, Kenya . The germplasm screened include CIMMYT Multiple Borer Resistance (MBR) and Multiple Insect Resistance Tropical (MIRT), germplasm developed during Insect Resistant Maize for Africa (IRMA) project, USDA Mississippi germplasm and subtropical elite germplasm. CIMMYT scientists have developed within two years several inbred lines and more than 200 single cross hybrids. The first generation of FAW hybrids were announced on the 23rd of December 2020 , including three FAW tolerant hybrids (FAWTH2001–2003), which passed the test of screening in the screenhouse, and later under natural infestation in both on station and on farm fields. The next step will be the national performance trials, variety release and registration by private sector (seed company) for the deployment in target geography in eastern and southern Africa. The same exercise is being done by IITA in West Africa to develop FAW maize resistant varieties and in Southern Africa by ICRISAT on sorghum. A lot of NARs in sub-Saharan Africa (especially in Uganda, Malawi) have also initiated germplasm screening to identify tolerant/resistance materials.
6.5 Transgenic approach to control FAW in Africa
The first transgenic Bt plants were introduced on the market in 1996 , whilst the first Bt maize for FAW control was introduced in the USA and Pueto Rico in 2013 . On the continent, Bt maize is currently commercially available only in South Africa, where regulatory authorities have overseen multiple approvals, with more than 20 years of deployment of such products. The MON810 event, which has been cultivated in South Africa since 1997 for the stem borer control, also confers partial resistance (50%) to FAW while the MON89034 event which has demonstrated efficacy for control of both FAW and stem borers has been cultivated in South Africa since 2010 . MON89034 is recommended for FAW control due to its high efficacy against the pest. The Water Efficient Maize for Africa (WEMA) project now TELA which is operating in 8 countries namely South Africa, Mozambique, Tanzania, Uganda, Kenya, Ethiopia, and Nigeria is to test and deploy the transgenic maize in Africa. Although Genetic engineering would provide an additional intervention that other countries struggling with FAW can explore alongside other integrated pest management practices, there are still contentions on the safety and sustainability of control using Bt maize. Many African countries also lack the legal frameworks for research on and deployment of Genetically Modified Organisms.
6.6 Chemical control of the fall armyworm
Chemical control is one of the key methods for controlling FAW in the Americas and Africa . Initial efforts to control FAW in Africa using chemicals relied on recommendations of effective pesticides from the Americas, leading to the purchase, distribution and application of several synthetic pesticides in many countries. Consequently, many maize farmers have adopted the use of pesticides, a practice that was rare before the advent of FAW. In this section, we review information on the use of chemical pesticides to control the FAW in selected countries on the continent as it is difficult to obtain country-specific information.
A variety of synthetic pesticides have been registered and recommended for control of FAW in different African countries. These include Carbamates, Organophosphates, Ryanodine Receptor modulators, Avermectins, Spinosyns, Oxadiazines, Nereistoxin and Pyrethroids (Table 2). Among the above, Pyethroids and Organophosphates are the most used (Table 2), followed by Avermectins, perhaps because of their availability and lower prices. Combination of different classes of pesticides are also on the market (Table 2). The combinations help increase the effectiveness, target spectrum, and reduce the speed with which pesticide resistance can develop. Pesticides shown in Table 2 below are approved and recommended by the respective African governments to control FAW. To date, several African countries do not have an official register for approved pesticides for control of the FAW. This may be in part due to the failure to test chemical pesticides for their efficacy. Nonetheless, we provide a review of research efforts towards use of chemical pesticides to control the FAW in Africa.
|Pesticide class||IRAC Group||WHO classification||Active ingredient(s)||Country of registration||Pesticide brand examples|
|Avermectins||6||II||Abamectin + Emamectin||Uganda ||Amdocs|
|Abamectin||Malawi ||Snowmectin 1.6 EC , Antario|
|IIV||Emamectin benzoate||Uganda ||Chlobenzo, Prove (EC), Dynamo (WG)|
|South Africa ||Emma, Proclaim, Promec 20EW, etc.|
|Zambia ||Prove (EC), Denim Fit 50WG|
|Benzoylureas||15||II||Lufenuron||South Africa ||Judge, Sorba|
|Kenya ||Heritage 5%, Legacy, Match|
|Diflubenzuron||South Africa ||Dimilin 25 WP, Dimilin 48 SC|
|Carbamate||1A||IB||Methomyl||South Africa ||Spitfire 900 SP, Cyplamyl 90 SP, Masta 900 SP|
|II||Carbosulfan||South Africa ||Marshal 48 EC|
|Kenya ||Marshall 250EC|
|14||Cartap hydrochloride||South Africa ||Ag-Tap 500 SP|
|Organophosphates||1B||II||Chlorpyrifos||South Africa ||Avi Klorpirifos, Agropyrifos, Pyrinex 480 EC|
|Malawi ||Chlorpyrifos 480 EC|
|Profenofos||Malawi ||Snoweron 500 EC|
|III||Mercaptothion + Malathion||South Africa ||Avi-Merkaptothion DP|
|Acephate||Kenya ||Lotus 75% SP, Ortran 97, Orthene pellet|
|Oxadiazine||22A||II||Indoxacarb||South Africa ||Doxstar Flo, Advance, Steward, Addition|
|Malawi ||Steward 150 EC|
|Kenya ||Merit 150 SC, Avaunt150 SC|
|Sudan ||Vaulent 150S C|
|Pyrethroids||3A||II||Beta- cypermethrin||South Africa ||Akito|
|Alpha- cypermethrin||Kenya ||Bestox 20 EC, Navigator 100 EC|
|Deltamethrin||Malawi ||Decis Forte, Deltanex 25 EC, Deltmax 25 EC|
|Zambia ||Decis, Decitab|
|28||Lambda-Cyhalothrin||Kenya ||Duduthrin Karate|
|3A||III||Teflubenzuron+Cypermethrin||Malawi ||WormAtak EC|
|NL||Gamma- cyhalothrin||Kenya ||Vantex 60 CS|
|Ryanodine Receptor Modulators||28||III||Flubendiamide||South Africa ||Belt 480 SC|
|Malawi ||Belt 480 SC|
|Kenya ||Belt 480 SC|
|U||Chlorantraniliprole||South Africa ||Coragen 20 SC, Prevathon, Mythic FN SC|
|Kenya ||Coragen 20 SC|
|Spinosyns||5A||U||Spinetoram||South Africa ||Delegate 250 WG|
|Kenya ||Radiant 120 SC|
|Nereistoxin analogue||14||U||Cartap hydrochloride||South Africa ||Ag-Tap 500|
|Avermectin+Diamide||6 and 28||II||Abamectin+Chlorantraniliprole||Kenya ||Voliam Targo 063|
|Benzoylureas+Avermectin||15 and 6||III||Lufenuron+Emamectin benzoate||South Africa ||Denim Fit|
|Malawi ||Proclaim Fit|
|Sudan ||Denim Fit 50%|
|Benzoylureas+Oxadiazine||15 and 22A||U||Novaluron+Indoxacarb||South Africa ||Plemax|
|Carbamate+Pyrethroids||1A and 3A||_||Benfuracarb+fenvalerate||South Africa ||Oncol Super 220 EC|
|Organophosphates+Pyrethroids||1B and 3A||II||Profenofos+Cypermethrin||Uganda ||Roket, Agro-Cypro, Supa Profenofos, Hitcell|
|Pirimiphos methyl+Deltamethrin||Malawi ||Ecoterex 0.5 GR|
|Zimbabwe ||Ecoterex 0.5 GR|
|Cypermethrin+Chlorpyriphos||South Africa ||Cyperfos 500 EC|
|Zambia ||Cyclone 505 EC|
|Pyrethroids+Neonicotinoids||3A and 4A||III||Lambda Cyahalothrin+Thiamethoxam||Uganda ||Striker, Engeo|
|Diamide+Neonicotinoid||28 and 4A||_||Chlorantraniliprole+Thiamethoxam||Zambia ||Fortenza Duo|
|Diamide+pyrethroid||28 and 3A||_||Chlorantraniliprole+Lambda cyhalothrin||South Africa ||Ampligo|
|Spinosyn+Benzoylureas||5 and 18||Spinetoram+methoxyfenozide||South Africa ||Uphold 360 SC|
|Spinosyns+Diamide||5 and 28||U||Spinotetramat 75+Flubendiamide 100||Sudan ||Belt extra 175 OD|
|Microbial disruptors of insect midgut membrane||II||U||South Africa ||Delfin, Florbac WG|
|South Africa ||Eco-Bb|
The rapid adoption of pesticides by farmers in Africa was mostly due to the distribution of free pesticides by the governments. Free distribution proved ineffective in most countries because;
Distribution was not matched with adequate training of farmers on proper pesticide usage.
Most of the distributed pesticides were not effective as they were never evaluated to determine the suitable application rates for the different agroecologies within the continent [2, 40]. This resulted in indiscriminate spraying by farmers.
Recommendations by governments of cheap chemical pesticides known to have developed resistance to FAW elsewhere. For example, Organophosphates and Pyrethroids-Pyrethrins pesticides to which FAW is reported to have developed resistance in the Americas (Prassana, 2018; Day et al., 2017; Yu, 1992; Yu, 1991; Yu, 1982; Giraudo et al., 2015; Flagel et al., 2018). The above has resulted in indiscriminate application of pesticides by farmers causing fears of likely resistance development in the near future [43, 51]. Although, there are no reports of development of pesticide resistance in FAW in Africa, there is evidence of samples of the pest from Kenya, Malawi and Uganda possessing mutations associated with resistance to organophosphates and carbamates [22, 23].
Furthermore, effectiveness of pesticide use in Africa is hindered because many of the countries in Africa lack listings of registered (government approved) pesticides for control of the FAW .
7. The future FAW management in Africa
The current invasion of the fall armyworm (FAW) in sub-Saharan Africa (SSA) and other parts of the world threatens food and nutrition security of many nations, and also poses challenges in the attainment of a number sustainable development goals (SDGs) including SDGs: 1 (no poverty), 2 (zero hunger), 3 (good health and wellbeing, 8 (decent work and economic growth) and 12 (protecting life on earth). Without sustainable management of this invasive pest, farmers’ efforts in increasing cereal productivity, most especially smallholder farmers in nations that rely on maize as a staple crop, will be futile. The previous sections provided detailed information on the biology and ecology of the FAW, and current management practices for curtailing damage and associated yield losses [98, 99, 100, 101, 102, 103]. Like most invasive insect pests, FAW management across the continent, has relied primarily on the use of pesticides and cultural interventions, but with minimal efforts on an IPM approach. In view of the pest status, threat posed to food and nutrition security, and the grave health and environmental footprints of indiscriminate use of pesticides, the need to formulate effective and sustainable management approaches is dire. This calls for formulation of an effective Pest Management Plan (PMP) at the national and regional levels. The plan should consider International Plant Protection Convention (IPPC) policies, the Pesticides and Toxic Substances Regulations, the Plant Pests and Diseases Regulatory Acts and, Environmental and Social Management Frameworks (ESMF). The components of such a plan may include: i) periodic scouting and review of FAW damage and impact to cereal productivity, ii) identification of interactions between FAW and other cereal insect pests belonging to the same family and consequential impact on productivity, iii) exploration of alternative ways of FAW management, with emphasis on environmentally friendly and socially acceptable approaches, and iv) identification of concerns related to pesticide use and recommendation of measures for enhanced public and occupational health and safety.
7.1 Interventions for sustainable management of fall armyworm in Africa
In planning for effective FAW management in the future, the following should be considered at national or regional levels;
Sufficient knowledge or data is a prerequisite for developing any sound action plan and management decision. According to FAO (2016), institutional capacity, effective policies and an enabling environment are key ingredients for the transformation and growth of the agricultural sector in the face of climate change. A lot of effort has been put in understanding the ecology of FAW and possible management practices, but much remains to be done. Equally important is the need to understand FAW behavior in the face of climate change. Thus, future FAW management will require generation of data that can be used for developing predictive models for determining future hotspots/outbreaks and decision-making. Addressing issues of pesticide resistance, will require proper planning, implementation of research activities, monitoring and evaluation, safeguards compliance, and regional engagement.
7.1.2 Collation and dissemination of research outputs
In addition to research, future FAW management should focus on effective dissemination of proven technologies, while leveraging on existing dissemination systems such as extension services of the Ministries of Agriculture and mass communication channels. Regional and/or continental exchange of information, knowledge and technologies will be key to managing this transboundary pest. Currently, however, the national dissemination systems in most African countries are not only weakened by poor research-extension linkages, but by low human capacity; lack of information and communication materials on recommended technologies; lack of harmonization of information packaging; inappropriate packaging of extension messages; limited use of mass communication channels; and inadequate training. Incorporating unique and modern approaches to transfer knowledge across the value chains, e.g., using training of trainers (TOT) approach, use of videos on social media platforms, radios, promoting strategic dialog and/or effective communication for knowledge transfer will play a critical role in sustainable management of FAW.
7.1.3 Capacity building
Currently, most scientists, extension officers and farmers lack knowledge on pest identification, economic impact assessment and management strategies. Capacity building interventions through scientific short and/or long-term trainings, as well as upgrade of research infrastructure (e.g., functional laboratories, greenhouses, containment facilities that can handle GMO materials) and information technology and knowledge management system are required to address the knowledge gaps for sustainable management of FAW on the continent. At grass-root level, hands-on trainings on FAW scouting, identification, safe use of pesticides and ecologically based integrated pest management strategies should be implemented through farmers’ field schools. Furthermore, government bodies like the Environmental Management Agencies, Agrochemical Associations, etc.) in different countries should take an active role in building the capacity of extension officers and farmers on good pesticide use and putting in place an effective monitoring system to ensure that only registered pesticides are being distributed to farmers, and that the formulations are maintained in their registered state (without re-formulation).
7.1.4 Enhanced coordination of stakeholders
Across the continent, the response to FAW outbreak by key actors (e.g., national governments, research scientists and regional bodies like FAO) was loosely coordinated. Moving forwards, regional and national government leaders should focus on ensuring that all essential FAW task forces and management coordination functions are effectively carried out.
7.1.5 Effective policy implementation
In most sub-Saharan Africa (SSA) countries, agricultural policies put emphasis on agricultural productivity, with the promotion of pesticide use to address the perennial low productivity placed among top pest management intervention strategies. Legislations on management of Plant Pests and Diseases that is often enforced by the Phyto-sanitary Services Department under the Ministry of Agriculture and The Pesticides and Toxic Substances Regulations (PTSR) do exist across the continent. Unfortunately, issues of improper and unsafe use of chemicals due to inadequate enforcement of regulations and lack of compliance to safety measures pose a serious threat to the ecosystem. Therefore, through the participation of key players (i.e., right institutional structures, systems and set of skilled personnel), the implementation of effective and targeted regulatory policies for improving agricultural sector, e.g., those that support subsidies, grants and tax credits, risk mitigation, market access, purchase of surplus produce from farmers must be strengthened, and applied in future FAW management plans.
While the African Union, through her Comprehensive African Agricultural Development Program has formulated strategies to improve agricultural productivity at regional level, FAW management plans are currently embedded within national agricultural and food security strategic plans but not at regional level. Thus, attempts to transform the African agriculture sector should focus on preparedness to respond to pest threats, specifically invasive transboundary pests like FAW and migratory locusts that the continent has witnessed recently. Such a preparedness plan should include, but not be limited to i) investments in proper policies, pest and disease management, extension and infrastructure, and ii) effective coordination of available resources for pest and disease management.
Addressing the FAW constraint in sub-Saharan Africa requires policy dialog and policy harmonization on key areas that affect the management of the pest at national and regional levels. For instance, issues of IPs/patents for new technologies, harmonization and operationalization of the pesticide regulatory system, implementation of biosafety regulations, etc. should be addressed at the regional level. Approved pesticides for FAW control at regional and national levels must comply with guidelines of the International Plant Protection Convention (IPPC) on Phytosanitary Measures for pest surveillance, risk identification, reporting and management and complement the recently published IPPC Guide to Pest Risk Communication. Equally such harmonized policies should support other global voices, such as The Stockholm and the Rotterdam Conventions that advocate for use of non-Persistent Organic Compounds (POPs), the Pesticide Action Network (PAN) and the Sustainable Agriculture Network (SAN). For example, the Pesticide and Toxic Substance Regulations, which advocates for using pesticides with: i) negligible adverse effects on humans and domestic animals in the treated areas; ii) effectiveness against the target species; iii) minimal effects on non-target species, especially damage to natural enemies, and the environment in general; iv) avoidance of pesticide resistance and resurgence, should be borne in mind during such policy dialogs and harmonization.