Abstract
The fall armyworm (FAW), Spodoptera frugiperda (J. E. Smith) (Lepidoptera: Noctuidae), originated from America but is reported recently from Africa and the Asia-Pacific. FAW has caused huge international concern since its outbreak in Africa since 2016 and in Asia since mid-2018. The chapter mainly reviews its global distribution, life cycle, identification characters, strains, host plants, nature of damage, economic damage, and integrated pest management strategies available. The pest completes its life cycle on maize in 30 days (in warm summer months); in cooler temperatures, it may extend up to 60–90 days. For effective management of fall armyworm, different tools, viz., cultural control, agronomic management, breeding for resistance, natural enemies, and eco-friendly insecticides, should be used in an integrated approach. As the insect is recently introduced to Africa and the Asia-Pacific, possible management strategies and future cases of action are discussed.
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8.1 Introduction
Invasive species are the biggest threat to the environment and cause ecological and economic losses (Wilson 1992; Evans et al. 2016). In the United States alone, invasive species have estimated to cause US$120 billion loss annually (Pimentel et al. 2005). The fall armyworm (FAW), Spodoptera frugiperda (J. E. Smith) (Lepidoptera: Noctuidae), originated from the Americas (Luginbill 1928; Sparks 1979) with wide host plants that include maize, sorghum, millets, rice, sugarcane, soybean, vegetables, and cotton (Prowell et al. 2004; Bueno et al. 2010; Padhee and Prasanna 2019). Fall armyworm is highly migratory in nature and has high fecundity, wide range of host plants, and voracious feeding behavior, without diapause. These characteristics make the fall armyworm a major destructive crop insect pests. Due to variation in weather conditions in the Americas, seasonal and continental movement of this pest from Canada to Argentina is noticed (Mitchell et al. 1991; Nagoshi and Meagher 2004, 2008). In eastern region of the United States, moth migration from the northeast to the southeast was noticed annually (Nagoshi et al. 2017).
Outside the Americas, FAW was first reported in West Africa in January 2016 (Goergen et al. 2016) and has spread to more than 40 countries across Africa (Prasanna et al. 2018a). In May 2018, this highly invasive insect pest was noticed for the first time in India on the maize crop in the Shivamogga and Davanagere districts and Karnataka state (Sharanabasappa et al. 2018a) and subsequently reported by Ganiger et al. (2018) and Shylesha et al. (2018).
8.2 Diagnostic Features and Life History
8.2.1 Diagnostic Features
The later instar larvae (fourth to the sixth instars) are brownish black with three white dorsal lines and alight lateral line. On the dorsal side of the larva, black tubercles are found which bear spines. The frons has white inverted “Y” line on the head, and four dark warts in a square form on the dorsal surface of the eighth abdominal segment (Fig. 8.1) (Prasanna et al. 2018a). Forewing of male is gray brown with white triangular patch at the apical region and circular spot at the center of the wing (Fig. 8.2e), whereas female has uniformly grayish brown forewings mottled with dark brown spots (Fig. 8.2f). The hindwings of both male and female are silvery white with a dark border (Oliver and Chapin 1981; Prasanna et al. 2018a; Sharanabasappa et al. 2018b; Ganiger et al. 2018).
As there is no diapause reported in this pest, overlapping generations are noticed in a cropping period (Sharanabasappa et al. 2020a), the same as in Africa where continuous host plants are available in off-season irrigated crops (Prasanna et al. 2018a). However, in America, where cooler climate exists, fall armyworm cannot survive; hence, it migrates to warmer regions in the winter months. Under tropical climates of Asia and Africa, where there is a bimodal pattern of rainfall, pest may thrive throughout the year causing economic losses.
Although both vegetative and reproductive parts are damaged by the fall armyworm, feeding injury results in whitish patches and ragged and elongated holes. Increased feeding further in the whorl may even affect the development of tassel. Extensive leaf damage due to S. frugiperda may significantly reduce the photosynthetic area, which may result in stunted plants and reduction in grain yield. At the reproductive stage, the larvae may bore through the side or top of the earhead and start feeding on kernels at milky stage, affecting the quality of the grain and yield.
8.2.2 Life History
Fall armyworm takes about 30 days to complete its life cycle on maize in warm summer months; however, in cooler temperatures, it may extend up to 60–90 days (Prasanna et al. 2018a). Detailed information on various stages of the pest is presented below.
8.2.2.1 Egg
The female adult lays about 1000 eggs in clusters on below or above the leaf surface of the maize plant, at the base of the plant, and also in whorls. The eggs are ventrally flattened. Immediately after laying, the eggs are of light green in color (Fig. 8.2a) for a day and then turn to golden yellowish and finally to black color before hatching. The female covers a layer of scales on the egg mass with moldy appearance. Egg hatching may take from 2 to 3 days with an average of 2.50 days (Prasanna et al. 2018a; Sharanabasappa et al. 2018b).
8.2.2.2 Larva
There are six larval instars with 14–19 days of larval duration, and color changes from instar to instar. First instars are green with a black head but it turns greenish brown during second instar. From third instar onward, larvae turn brown with three dorsal and lateral white lines (Fig. 8.2b) (Prasanna et al. 2018a; Sharanabasappa et al. 2019b, ICAR – IIMR 2019).
8.2.2.3 Pupa
Pre-pupa stops feeding and turns bright brown during pupal stages (Fig. 8.2c). Pupation takes place in the soil, and pupal period ranges from 9 to 12 days (Prasanna et al. 2018a; Sharanabasappa et al. 2019b). Pupal sexing can be done by looking at the genital opening. The distance from the genital opening to the anal slot can be used to distinguish the female and male pupa. The distance from the genital opening to the anal slot is more in female pupa than in the male pupa (Fig. 8.2d).
8.2.2.4 Adult
The adult longevity includes preoviposition, oviposition and post-oviposition periods ranged from 3 to 4, 2 to 3, and 4 to 5 days, respectively. In captivity, each female lays 835 to 1169 eggs with an average of about 1000 eggs. The total life cycle of male and female fall armyworm ranges from 32 to 43 and 34 to 46 days, respectively (Sharanabasappa et al. 2018b).
The female survives for 10.80 days with a range of 9–12 days compared to the male (8.20 days) with a range of 7–9 days. The average wingspan of female is 3.20 cm with a range of 3.00 to 3.4 cm, while it is 3.25 cm with a range of 3.00 to 3.50 cm in male (Sharanabasappa et al. 2018b).
Temperature and developmental rate of fall armyworm are linearly related between 18°C and 30°C and 26°C and 30°C, respectively. Studies demonstrated that 26°C and 30°C are the optimal range for egg, larval, and egg-to-adult development and lower larval maturity and the optimum temperature with the fastest larval development rate, and lowest mortality was at 30°C as reported by Du Plessis et al. (2020) (Table 8.1).
8.2.3 Strains of Fall Armyworm
FAW has two strains that are morphologically similar but differ in their host plant preference. The rice strain (R-strain) prefers to feed on rice, Bermuda grass, and other small grasses, whereas the corn strain (C-strain) prefers to feed on maize, sorghum, and other large grasses (Pashley et al. 1985; Pashley 1986; Pashley et al. 1987). These two strains do not have any clear biological attributes even though differences are evident in the whole genome, transcriptome, etc. (Gouin et al. 2017; Silva-Brandao et al. 2017). Mahadevaswamy et al. (2018) reported the presence of R-strain in population sampled from different parts of India using mtCOI gene, but this requires further validation. Maruthadurai and Ramesh (2020) reported the R-strain in the FAW population from Goa. It must be noted that the FAW population in India preferentially damages maize, sorghum, and millets than rice. Hence, there is a confusion how mtCOI-detected R-strain is preferring to feed on rice in India.
In the Americas, the commonly used markers to identify morphologically indistinguishable C-strain and R-strain populations are mitochondrial cytochrome oxidase subunit I (COI) and nuclear triosephosphate isomerase (Tpi). Fall armyworm has two strains collections from Africa and India were reported to be R-strain detected by COI marker, although collections tested to date are from C-strain-preferred crops. When Tpi marker was used, >95% of the specimens were identified as C-strain. This indicates that Tpi marker is the ideal marker for identification of strains in Asian population. However, the presence of the R-strain in the Eastern Hemisphere needs constant watch, as it prefers to attack major host such as rice (Nagoshi et al. 2020).
The studies also suggest that fall armyworm from Africa and Asia has genetic similarity indicating invasion occurred from small number of population from the Western Hemisphere. The confusion of R-strain × C-strain might be due to inter-strain mating (Nagoshi et al. 2020).
Genetic evidence also suggests that FAW from Africa, India, Myanmar, and China shows that populations share a common and recent origin that derived from a small number of introductions (as few as one) from the Western Hemisphere. Nagoshi et al. (2020) provided two lines of evidence that suggest that a single strain predominates in the Eastern Hemisphere and that it is most likely the C-strain. Overall, they suggested that the FAW from Africa is behaving as expected for the C-strain, with the R-strain a minor presence or perhaps even absent. They also suggested that in Myanmar, China, India, and most of Africa, the COI strain marker is in disagreement with both Tpi and host plant. One way this could have occurred might be linkage between the mitochondrial COI marker and strain identity that was disrupted by inter-strain mating. Since mitochondria are maternally inherited, mating between an R-strain female and C-strain male would produce COI-RS hybrid daughters, which if they also mated with C-strain males would produce COI-RS progeny in a C-strain (including TpiC) background (Nagoshi et al. 2020).
Hybrid daughters may be produced with COI-RS strain male mates, as the mitochondria are maternally inherited. There is a need for comprehensive genetic analysis for invasive population to understand the strains and the host plants attacked. However, recent studies (Nagoshi et al. 2019, 2020) suggest the need for more extensive sampling of FAW on many more host plants across Asia for more reliable detection of host-associated differences.
8.3 Nature of Damage
Fall armyworm moths are nocturnal and hide during the daytime in the whorls of the maize plant. They are more active during the evening hours. Female moth lays eggs above/below the leaf surface of the maize plant, at the base of the plant, and also in whorls. Immediately after hatching, the neonate larvae secrete a silken thread and spread to the neighboring plants through wind. Early instars (1–3 instar stages) feed on the leaves, causing whitish patches appearing as “scratches” on the leaf surface (Fig. 8.1b). Grown-up caterpillars feed on leaf tissues resulting in ragged and elongated holes on leaves leading to sickly appearance. A very diagnosable symptom of attack is the presence of lumps of fecal matter in the whorls (Fig. 8.1c). Fall armyworm incidence starts when the crop is around 10–20 days after sowing. In early stage of the crop, 2–3 larvae are noticed feeding on the leaves, and in later stage of the crop, one or two later instar larvae per plant are noticed when the crop is around 30 to 40 days old. When two larvae are found in a single whorl, their feeding sites are different because in fall armyworm cannibalism is noticed. The early instar enters the cob through silk, whereas the later instar larva bores the husk and goes inside the cob and feeds on the kernels (Fig. 8.3a).
8.4 Global Distribution and Economic Damage
FAW has been found in 43 countries of Africa, 41countries in North America, 28 countries in Central America, and 32 countries in South America (Dively 2018). The pest is now widely prevalent in the Asia-Pacific region, including India, Yemen, Bangladesh, Sri Lanka, Thailand, Myanmar, China, Indonesia, Laos, Malaysia, Vietnam, Republic of Korea, Japan (FAO 2019), Nepal (Bajracharya et al. 2019), Indonesia (CABI 2019), and the Philippines (Navasero et al. 2019). Now the presence of this pest is reported in all states of India, except for a few northern states (Rakshit et al. 2019). Fall armyworm has spread to 26 provinces of China, the second biggest maize-producing country in the world after United States (Jiang et al. 2019). Recently, in February 2020, the pest has been reported in Australia (FAO 2020a; QGDAF 2020).
FAW is a highly invasive insect pest, with adult moth dispersal strongly influenced by wind and environmental conditions. FAW moths were reported to travel more than 100 km per day and nearly 500 km before egg laying, and they can move to newer places very quickly under favorable wind conditions. FAW is highly polyphagous; Montezano et al. (2018) reported a host range of 353 plant species from 76 plant families, principally Poaceae (106), Asteraceae (31), and Fabaceae (31). Despite such a broad host range, maize is undoubtedly the most widely preferred host by the pest. In Africa as well as in Asia, FAW damage has been mostly reported on maize, followed by a few other crops, like sorghum, millets, and vegetables. FAW has not adversely affected rice, despite its extensive cultivation in West Africa and many other sub-Saharan Africa countries (Rwomushana et al. 2018).
Yield losses due to FAW were estimated around 40 % in Honduras in Central America (Wyckhuys and O’Neil 2006) and 72 % in Argentina (Murúa et al. 2006). According to FAO, Brazil alone spends US$600 million annually on FAW management (Wild 2017). Abrahams et al. (2017) reported that FAW has the huge potential to cause 21% to 53% reduction in annual maize production (or US$2,481 to US$6,187 million economic damage) in 12 maize-producing African countries. In Africa, the maize losses were estimated at US$2.5 to 6 million due to fall armyworm in 2017 (Day et al. 2017).
8.4.1 Crop Damage in India
Maize is the third most important cereal crop after rice and wheat, both in terms of area and production, registering maximum growth rate among food crops. In India, maize is grown in an area of 9.2 million hectares with a production of 27.82 million metric tonnes per year (FAO 2018). As reported by DMR (2012) and Chaudhary et al. (2012), the utilization pattern for maize in India includes mainly poultry feed (52%), human food (24%), animal feed (11%), and industrial processing (12%). The maize area affected due to fall armyworm in India in 2018–2019 was reported to be about 2.45 lakh hectares (Anonymous 2019). In India, it primarily feeds on maize (Fig. 8.3b), fodder maize, sweet corn, baby corn, and also other hosts, like sorghum (Fig. 8.3c), pearl millet (Fig. 8.3d), finger millet, sugar beet, and grasses, as reported by different workers (Table 8.2). In addition, FAW feeding was also reported on sugarcane (Fig. 8.3e) (Chormule et al. 2019) but not causing significant yield loss.
8.5 Integrated Pest Management (IPM)
The aim of IPM is to economically reduce the pest populations using suitable techniques and methods that minimize hazard to the environment, including people. IPM requires the farmers or farm advisors to have significant knowledge of agronomic and pest management approaches to implement an effective program based on local farming conditions (Prasanna et al. 2018a). The experiences so far in the Americas as well as Africa clearly show that there is no specific solution or magic bullet for effectively and sustainably controlling FAW. An IPM strategy based on science, inclusiveness, and balanced strategy is the need of the hour (Fig. 8.1). Emergency responses exclusively based on the use of synthetic pesticides have shown satisfactory results but need to be economically viable, to be used as per label claims, and must be safe for human health, biodiversity, and the environment (Fig. 8.4).
An effective IPM strategy for control of FAW will employ a toolbox approach, with different tools used in combination based on the cropping system, availability of technologies, and socioeconomic conditions of the farming communities. The IPM toolbox for FAW management could potentially include cultural control, agronomic management, host plant resistance, biological control, and environmentally safe synthetic biopesticides to protect the crops from economic injury while minimizing negative impacts on people, animals, and the environment (Prasanna et al. 2018a).
8.5.1 Monitoring, Surveillance, and Early Warning
Tracking and monitoring the spread of FAW across the country, region, and continent in a timely manner are critical if good decisions relating to control and management are to be made. Standard methodologies for field scouting and collection of pheromone trap data are available (FAO 2020b; McGrath et al. 2018). In Africa, bucket traps and locally constructed traps are showing promise, while delta traps were found to capture fewer FAW moths. Determination of the most effective pheromone lure for FAW is less straight forward. While many pheromone lures attract about the same number of moths, the number of nontarget moths can vary significantly. In India, funnel-type pheromone traps are used for monitoring the FAW. Since the pest has invaded recently in India, studies on pheromone trap catches are going on. The maximum number of trap catches of FAW was recorded during 46th and 45th standard weeks in maize and sorghum crops (Jaba et al. 2019). There is an urgent need to develop FAW-species-specific pheromone lure with accurate pheromone blend ratio for effective pheromone lure catches.
Given the visible nature of FAW, formal surveillance (including the use of appropriate pheromone traps) should be complemented by use of community-based crowd-sourcing techniques. Similarly, understanding and predicting dispersal patterns are essential if any early warning system is to be developed for effective control. Progress has been made on FAW environmental suitability models which can help to prioritize and improve scouting and trapping activities (Early et al. 2018). FAO established a Fall Armyworm Monitoring and Early Warning System (FAMEWS), which consists of the FAMEWS mobile app that was launched in March 2018 and a global platform that was established in July 2018.
8.5.2 Mechanical, Cultural, and Agroecological Management
The female moth lays up to 1500 eggs. These eggs are seen with naked eyes, and thus, farmers can identify and kill these egg masses with adequate training, as to prevent the caterpillars from damaging the crops. Manipulation of planting dates to ensure that the most susceptible stages of crop growth do not coincide with periods of peak moth activity is a well-known strategy to control lepidopteran pests. Planting early and adhering to regional planting calendar (avoiding late planting) will allow the maize crops to mature before buildup of high pest population. Tillage may destroy the pupae of lepidopteran pests (particularly in the case of FAW), as the pupae reside in the soil. Proper fertilization may also reduce plant damage by increasing plant defenses or increase it by making the plant more attractive to ovipositioning females. Intercrops may reduce crop infestation by lepidopteran pests through four possible ways: (i) by decreasing the movement of the caterpillars between maize plants, (ii) by decreasing the oviposition on maize plants, (iii) by emitting volatiles repelling ovipositioning females, and (iv) by hosting natural enemies.
The abundance of wide-ranging natural enemies of FAW (e.g., predatory arthropods, insectivorous birds, and/or bats) is a function of the availability of suitable habitat in the landscape, including hedgerows and non-crop habitat. Zero tillage and mulching may also create a favorable habitat for natural enemies and provide them with alternative prey. Push-pull strategy is another potential option for agroecological management of FAW (Midega et al. 2018).
8.5.3 Host Plant Resistance
Integrated pest management involving host plant resistance is a very important component against fall armyworm (Prasanna et al. 2018b).
Maize germplasm with naturally occurring or “native” genetic resistance to FAW was developed by CIMMYT in Mexico, where the pest was prevalent for several decades. Several research organizations such as CIMMYT (Mexico), EMBRAPA (Brazil), USDA-ARS (Mississippi), and universities in the United States led to the development of number of improved maize inbred lines with partial resistance to fall armyworm (Prasanna et al. 2018b). Similarly, sorghum and pearl millet germplasm also have native genetic resistance to sorghum stem borer; it may also be suitable for FAW developed by ICRISAT in India and Africa. Molecular biology tools now provide great potential for accelerating the development of new and promising varieties that could provide tolerance/resistance to fall armyworm and a host of other biotic stresses. Breeding for native genetic resistance to FAW is a medium- to long-term strategy and requires effective coordination and resources from the national partners and international organizations, like CIMMYT.
Transgenic/Bt maize producing endotoxins from the soil bacterium Bacillus thuringiensis (Bt) is one of the potential options for controlling a lepidopteran insect pest, like FAW. Bt maize technology is one of the most effective options to manage the FAW in both the United States and Brazil. In Africa, the TELA project has been testing Bt maize under confined field trials (CFTs) in six African countries to demonstrate the safety, efficacy, and yield benefits of the Bt maize under African conditions. Some of the African regulatory agencies have built capacity for science-based decision-making to address issues and societal concerns regarding Bt technology safety, effectiveness, and performance. Pyramiding transgenes with different novel modes of action (e.g., Cry + Vip genes) could be more effective and durable compared to single-gene deployment. Fast-tracked release of elite Bt maize varieties with FAW resistance could provide another powerful option in the IPM toolbox for FAW management. This, however, needs to go hand in hand with proper stewardship and insect resistance management to ensure durability of the technology.
8.5.4 Biological Control
Identification and use of natural enemies form basic component in IPM. Wherever necessary, inundative/augmentative release of well-validated biological enemies against FAW (e.g., Trichogramma sp. and Telenomus sp.; the egg parasitoids) should be taken up as a priority by public and private sector institutions in India. Several natural enemies have already been identified in African countries and in India, with reasonable levels of efficacy. In addition to biological control agents, bio-rational pesticides (like neem-based preparations) could also be potentially incorporated into the IPM-based strategies.
Survey carried out in the East African countries (Ethiopia, Kenya, and Tanzania) revealed four hymenopteran (Cotesia icipe Fernandez-Triana and Fiaboe (Braconidae), Chelonus curvimaculatus Cameron (Braconidae), Coccygidium luteum Brullé (Braconidae), Charops ater Szépligeti (Icheneumonidae)) and one dipteran (Palexorista zonata (Curran) (Tachinidae)) parasitoids (Sisay et al. 2018). With the exception of C. curvimaculatus, an egg-larval parasitoid, the rest are larval parasitoids. All these four species are native to Africa and not reported before from Africa or North and South America. Among these, one of the dominant larval parasitoids, C. icipe, with the high parasitism can be used for the management of fall armyworm (Sisay et al. 2018).
The two year surveys of fall armyworm natural enemies in maize and sorghum fields in Nigeria reported the egg parasitoids Trichogrammatoidea sp., Trichogramma sp., and Telenomus sp. and one egg-larval parasitoid Chelonus sp. and the other four larval parasitoids, viz., Cotesia sp., Charops sp., and unidentified ichneumonid and tachinid fly (Amadou et al. 2018).
The fungal pathogens like Metarhizium anisopliae and Beauveria bassiana are found effective against the eggs and second instar larvae of fall armyworm. Under laboratory conditions, M. anisopliae caused egg mortalities of 79.5%–87.0%, and B. bassiana recorded mortality of 30% to second instar larvae. The total mortality of eggs and early-stage larval mortality with M. anisopliae was as high as 96% with some fungal isolates (Akutse et al. 2019). Shylesha et al. (2018) recorded the egg parasitoids, viz., Telenomus sp., Trichogramma sp., Glyptapanteles creatonoti (Viereck), Campoletis chlorideae Uchida (Ichneumonidae), and Cotesia ruficrus on S. frugiperda larvae collected from the maize fields in Karnataka, India. Navik et al. (2019) recorded the natural parasitism (25.64%) by the Trichogramma sp. on fall armyworm eggs from Karnataka. Gupta et al. (2019) reported Cotesia ruficrus as an indeterminate larval-pupal ichneumonid parasitoid on fall armyworm, and the emergence of C. ruficrus adults from FAW larva is 11–29 wasps/larva. Sharanabasappa et al. (2019a) recorded larval parasitoids, namely, Coccygidium melleum (Roman), Odontepyris sp., and Eriborus sp. from Karnataka. In kharif 2019, the activity of two egg parasitoids, namely, Trichogramma sp. and Telenomus remus, was recorded from Shivamogga and Davanagere districts of Karnataka (Sharanabasappa et al. 2020a). Two predatory pentatomids, Eocanthecona furcellata and Andrallus spinidens, feeding on the larva of fall armyworm are reported by Shylesha and Sravika (2018). During the monsoon season (kharif) 2018, natural infestation of entomopathogenic fungi, Metarhizium (=Nomuraea) rileyi was noticed on S. frugiperda with its infection ranging from 1.87% to 18.30% (Mallapur et al. 2018) and 10% to 15 % (Sharanabasappa et al. 2019a). A comprehensive list of natural enemies reported from India is in Table 8.3.
8.5.5 Pesticide and Pesticide Risk Management
8.5.5.1 Pesticide
Insecticides are the necessary components in the insect pest management. The judicious use of insecticides is necessary for proper and effective pest management of the pest and least disturbance to the natural enemies and to the environment. The field efficacies of different insecticides against fall armyworm were investigated by many workers.
Another major issue with fall armyworm is the development of quick resistance to insecticides because of its behavioral and physiological factors (Yu 1991). Gutiérrez-Moreno et al. (2019) studied the field-evolved resistance of the fall armyworm to different insecticides. The LD50 values for flubendiamide, chlorantraniliprole, emamectin benzoate, and spinetoram against fall armyworm populations are collected from Mexico and Puerto Rico. The LD50 values of Puerto Rico are higher as compared to Mexico values because these insecticides are being used against FAW from many years in Puerto Rico.
Belay et al. (2012) studied the efficacy of different insecticides against FAW larvae under laboratory conditions. The insecticides like spinetoram, acephate, and thiodicarb recorded maximum (≥60%) larval mortality as compared to lambda cyhalothrin and chlorantraniliprole. Similarly, Sisay et al. (2019) observed the insecticidal mortality to larvae of FAW under laboratory conditions showed that lambda cyhalothrin 5 EC recorded 77.8% larval mortality, and the next best were chlorantraniliprole plus lambda cyhalothrin 150 SC (62.2% mortality); spinetoram 120 SC recorded highest (61.1%) larval mortality and chlorantraniliprole 200 SC (60% mortality). At 48 and 72 h after treatment, spinetoram 120 SC caused the highest larval mortality of 96.7% and 100% larval mortality, respectively, whereas lambda cyhalothrin 5 EC recorded 96.7% mortality 48 h and 72 h after treatment applications. At present, the Central Insecticide Board and Registration Committee, India, recommended the ad hoc use of chlorantraniliprole 18.5 SC, thiamethoxam 12.6% + lambda cyhalothrin 9.5% ZC, emamectin benzoate 5 SG, and spinetoram 11.7 SC for fall armyworm management (DPPQS 2019). Mallapur et al. (2019) evaluated the efficacy of some insecticides both in laboratory and field experiments. The laboratory results revealed that spinetoram 11.7 SC and emamectin benzoate 5 SG were significantly superior over other treatments with 100% mortality at 60 hours after treatment. Under field conditions, spinetoram 11.7 SC, emamectin benzoate 5 SG, and spinosad 45 SC reduced the larval population to 98.13, 96.26, and 96.26 %, respectively, at 7 days after treatment. Muralimohan and Dileepkumar (2019) studied the efficacy of different insecticides as both sprays and poison baits (applied in whorls of infested plants). Spinetoram 11.7 SC, chlorantraniliprole 18.5 SC, and novaluron 10 EC recorded highest larval mortality (93.53% to 96.76% reduction over untreated control) under laboratory conditions. Field studies suggested that bait application was as effective as foliar sprays involving same insecticide. The results indicated that greener molecules with a waiting period of < 3–5 days were very effective as baits, and cost of plant protection was substantially low when used as baits (up to 42% cost reduction). This finding provides an opportunity for the growers not only to reduce the cost of protection but also to make the food safe for consumption, particularly as fodder maize fed to the animals. Among the insecticides and biopesticides tested, thiodicarb 75% WP at 1g per lit, emamectin benzoate 5 SG at 0.5g per lit, and spinetoram11.7 SC at 0.5 ml per lit were found to be very effective against FAW, while pongamia oil at 6ml per lit of water was also found to be most effective among the biopesticides (Jaba et al. 2019). Similarly, Sharanabasappa et al. (2020b) found that chlorantraniliprole 18.5 SC at 37 g ai per ha, emamectin benzoate 5 SG at 12.5 g ai per ha, and spinetoram11.7 SC at 29.2 g ai per ha are suitable insecticides in managing the fall armyworm.
8.5.5.2 Pesticide Risk Management
Pesticides are classified based on hazards and risks which are used for the control of fall armyworm (Jepson et al. 2018). The suggested requirements for pesticide recommend the use of products that can be used with minimal protective clothing (PPE), which allows the reentry to the field, a day or less after spray or treatment. While there are plenty of crop protection products available across Africa and Asia, not all of them may be effective in controlling FAW. Products that farmers have been using range from chemicals, such as emamectin benzoate, chlorpyrifos, chlorantraniliprole, cyantraniliprole, emamectin benzoate, and lambda cyhalothrin, to biological, such as Bt, spinosad, spinetoram, and plant and biological extracts. Application of insecticides should be done late in the evening when the larvae are active (not hiding within the whorls); the larvae mostly feed in the early morning or at night when temperatures are not high and when there is no bright light.
Biological pesticides and natural enemies have been extensively studied, and a guide to candidate FAW biopesticides and biological control agents is published recently (Bateman et al. 2018). These include pesticides registered in 30 countries, 11 in Americas and 19 in African countries. Among the fifty biopesticide reported, twelve are found to be effective against FAW outside Africa, and these biopesticides are already registered to manage other pests in some African countries. A similar inventory needs to be drawn up soon in Asian countries.
8.6 Conclusions
Within a short span of 3–4 years, fall armyworm has spread to several countries across Africa and the Asia-Pacific, causing huge damage to the crops, especially maize, sorghum, and pearl millet in particular affecting the food surety, income, and subsistence of million farmers. Intensive research is required for developing economic thresholds, besides various aspects of the biology and behavior of fall armyworm in continents like Africa and Asia. Besides monitoring and surveillance, environmentally sustainable fall armyworm management requires effective integration of various approaches, including biological control, environmentally safe pesticides including biopesticides, host plant resistance, and agroecological management. In summary, fall armyworm poses a complex challenge and needs to be managed through well-coordinated, inter-institutional, and multidisciplinary efforts.
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Deshmukh, S.S., Prasanna, B.M., Kalleshwaraswamy, C.M., Jaba, J., Choudhary, B. (2021). Fall Armyworm (Spodoptera frugiperda). In: Omkar (eds) Polyphagous Pests of Crops. Springer, Singapore. https://doi.org/10.1007/978-981-15-8075-8_8
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