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Egonyu, J.P.;  Baguma, J.;  Martínez, L.C.;  Priwiratama, H.;  Subramanian, S.;  Tanga, C.M.;  Anankware, J.P.;  Roos, N.;  Niassy, S. Key Oil Palm Pests and Their Managements. Encyclopedia. Available online: https://encyclopedia.pub/entry/39688 (accessed on 03 May 2024).
Egonyu JP,  Baguma J,  Martínez LC,  Priwiratama H,  Subramanian S,  Tanga CM, et al. Key Oil Palm Pests and Their Managements. Encyclopedia. Available at: https://encyclopedia.pub/entry/39688. Accessed May 03, 2024.
Egonyu, James P., John Baguma, Luis C. Martínez, Hari Priwiratama, Sevgan Subramanian, Chrysantus M. Tanga, Jacob P. Anankware, Nanna Roos, Saliou Niassy. "Key Oil Palm Pests and Their Managements" Encyclopedia, https://encyclopedia.pub/entry/39688 (accessed May 03, 2024).
Egonyu, J.P.,  Baguma, J.,  Martínez, L.C.,  Priwiratama, H.,  Subramanian, S.,  Tanga, C.M.,  Anankware, J.P.,  Roos, N., & Niassy, S. (2023, January 03). Key Oil Palm Pests and Their Managements. In Encyclopedia. https://encyclopedia.pub/entry/39688
Egonyu, James P., et al. "Key Oil Palm Pests and Their Managements." Encyclopedia. Web. 03 January, 2023.
Key Oil Palm Pests and Their Managements
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Oil palm, Elaeis guineensis Jacq. (Arecales: Arecaceae), is a multipurpose plantation crop that is extensively grown in the humid tropics across Asia, Africa and the Americas for palm oil and other uses such as sauces, soap, wine, fertilizer (ashes), roofing (leaves), building material (trunk), medicines (roots), and ornamental purposes. Oil palm is attacked by numerous insect species globally, including defoliators, leaf/fruit scrapers, borers and sap feeders. The common oil palm pest management methods include synthetic insecticides, biopesticides, semiochemical lures, cultural practices, and integrated approaches.

Borers Defoliaters Leaf/Fruit scrapers Sap feeders synthetic insecticides biopesticides semiochemical lures cultural practices integrated pest management

1. Introduction

Oil palm, Elaeis guineensis Jacq. (Arecales: Arecaceae), is a multipurpose plantation crop that is extensively grown in the humid tropics across Asia, Africa and the Americas for palm oil and other uses such as sauces, soap, wine, fertilizer (ashes), roofing (leaves), building material (trunk), medicines (roots), and ornamental purposes [1]. About 40% of all traded vegetable oil globally is palm oil [1], and this oleaginous species has the potential to produce 4–20 times more oil per hectare of land than any other oil crop [2]. As such, oil palm production has rapidly grown more than 35-fold from only 2 million tonnes in 1970 to 71 million tonnes in 2018 [2]. There are more than 140 palm oil importing countries of which India, China and the United States of America lead the market with more than nine, five and one million tonnes of palm oil imports in 2017, respectively [2].
Although a wide range of tropical climates and soils in about 20 countries that lie between 10° N and 10° S of the equator are conducive for oil palm cultivation, Indonesia and Malaysia account for more than 84% of oil palm production globally [1][2]. Palm oil production in Latin America, which accounts for 6.4% of global production, has increased by almost 60% in the last ten years to 4.6 million tonnes in 2020/21 [3]. In Africa, the oil palm belt runs from the southern latitudes of Guinea, Sierra Leone, Liberia, Ivory Coast, Ghana, Togo, Benin, Nigeria, and Cameroon to Equatorial Guinea and the Congo [4]. Oil palm requires maximum and minimum temperature ranges of 29–33 °C and 22–24 °C, respectively; total annual rainfall of at least 2000 mm; and acidic sandy, fine clay or silty loam soils [5].
Although peak palm oil yields of 12 t ha−1 yr−1 have been achieved in small plantations against a theoretically simulated yield potential of 18.5 t ha−1 yr−1, average oil palm productivity worldwide has stagnated around 3 t ha−1 yr−1 [6]. The suboptimal oil palm productivity is attributed to climatic factors such as rainfall and temperature, nutrient deficiency (especially potassium and nitrogen), unsuitable ground vegetation, soil characteristics (e.g., depth and structure), genotypes, pests and diseases, among other factors [6][7]. The intensive monoculture of oil palm makes it highly susceptible to a range of indigenous insect pests due to reduced crop biodiversity which supports natural enemies of the pests [7-[8].

2. Overview of Key Oil Palm Pests and Their Managements

Oil palm is attacked by numerous insect species globally. Twenty-five out of thirty-six of the species which defoliate oil palm are lepidopteran larvae, dominated by limacodids, nymphalids, psychids and elachistids. Other oil palm defoliators are coleopterans and tettigoniids. Oil palm borers are dominated by larvae of curculionids in the genus Rhynchophorus, but it is also bored by adult scarabids and larval brachodids and castniids. Oil palm sap suckers are dominated by members of the hemipteran family, Tingidae. Leaves of the oil palm are scraped and/or mined by chrysomelids.

2.1. Defoliators

Oil palm leaves contain a high content of indigestible cellulose fibers and a low nutritional value, therefore, a restricted number of insect orders such as Orthoptera, Phasmatoptera, Lepidoptera, Coleoptera, and Hymenoptera have evolved as palm defoliators [9]. The larval stages of these insects adapt to the low nutritive value of oil palm leaves by developing relatively slowly, always for more than a month. For example, larvae of the leaf defoliator Leucothyreus femoratus Burmeister (Coleoptera: Scarabaeidae) takes 92–113 days to develop [10]; those of Acharia fusca Stoll (Lepidoptera: Limacodidae) take 76–94 days [11]; and those of Metisa plana Walker (Lepidoptera: Psychidae) take 72 days [12]. There are, however, some oil palm defoliators with short larval durations, e.g., Acria meyricki Shashank and Ramamurthy (Lepidoptera: Depressariidae) with approximately 20 days [13]. The damage by defoliators is exacerbated by dry conditions, probably due to suppression of the activities of natural enemies such as entomopathogens, parasitoids and predators during dry spells [9].

2.1.1. Nettle and Slug Caterpillars

The nettle and slug caterpillars (Lepidoptera: Limacodidae) are the most-widespread oil palm defoliators in all oil palm growing areas of the world, with at least 22 species reportedly reaching outbreak levels and attacking different parts of the crown [14]. For example, damage by Euprosterna elaeasa Dyar (Lepidoptera: Limacodidae), and other Neotropical lepidopteran defoliators also facilitates the spread of oil palm Pestalotiopsis fungal pathogen [15]. The lifecycle of E. elaeasa has nine larval instars which feed on the mesophyll until the fourth instar, and then on the entire leaf blade thereafter [16]. Euprosterna elaeasa is commonly controlled using synthetic insecticides, although insecticide-resistance has been noted [17]. Essential plant oils, notably from Cymbopogon martinii [18], insect growth regulators such as fenoxycarb, methoxyfenozide, pyriproxyfen, and tebufenozid [19], the nucleopolyhedrosis virus EuelNPV [20], and Bacillus thuringiensis Berliner (Bt) strains [19] have demonstrated toxicity and/or antifeedant activity against E. elaeasa at levels that are comparable or superior to conventional insecticides, under controlled trials, and are recommended for evaluation as components of integrated approaches against the pest in the field [20][21].

2.1.2. Bagworms

The bagworm family (Lepidoptera: Psychidae) which includes approximately 1000 described species in 300 genera and ten subfamilies is well reviewed by Rhainds and colleagues [22]. Embryonic development in bagworms is usually completed within a month under tropical and subtropical conditions. Upon hatching, phytophagous neonates either remain to feed on the mother host plant or disperse by wind, vehicles, animals, or humans, aided by silk threads which they secrete from their posterior openings. Before starting to feed, first instars construct a protective self-enclosing bag using plant tissue or organic and inorganic debris within which the larval development is completed. The destructive larval stage lasts for about 1–7 months under tropical and subtropical conditions. Prior to pupation, the larvae tightly attach the anterior portion of their bag onto a substrate. Most species of bagworms feed on a broad range of plants during their larval stages. Several species of bagworms have been reported attacking oil palm in Asia since the start of the plantation industry [14], and others such as Clania tertia Templeton and Manatha conglacia Haettenschwiler continue to expand their host range to become new serious pests of oil palm [23][24].
Mahasena corbetti Tams is one of the large bagworm species which is endemic to Malaysia, but it has spread across the Paleotropical region [22]. The pest reportedly causes 40–50% losses in oil palm yields in Malaysia and Indonesia if not managed, with severe infestation of preferred host plants such as Fabaceae and Arecaceae (including oil palm) being fatal [25]. Owing to its invasiveness and a wide host range comprising 37 plant genera from 21 families, M. corbetti is considered a quarantine pest in many countries such as India, Singapore, Sri Lanka and Malaysia, among others [26][27][28][29]. Adult males of M. corbetti are black to brown with white scales on some of them; while females are wingless, cylindrical, and creamy-white with either no or greatly minimized appendages [27]. Larval feeding causes yellowing and subsequent dying and falling of leaves [30]. Mahasena corbetti is highly prolific, with each female laying over 3000 eggs, hence making the pest efficient at creating outbreaks [26]. It is quite difficult to control large M. corbetti outbreaks using aerial sprays of contact insecticides because its larvae cryptically feed on the abaxial surface of fronds which the insecticides cannot easily reach [31]. Therefore, palm trunk injections with systemic insecticides are required to effectively control the pest. Application of Bt to control M. corbetti has also not been effective [32]. Though laborious, hand-picking of M. corbetti larval bugs which actively move during bright sunlight can be effective against the pest [27].
Other bagworms, such as M. plana and Pteroma pendula Joannis are significant oil palm defoliators across Southeast Asia [12][33][34]. Application of both Bt-based biopesticide and synthetic insecticides (chlorantraniliprole, cypermethrin and flubendiamide) in Malaysia using a motorized backpack mist blower caused 70–83% mortality of M. plana and were able to suppress the pest population for a month after treatment [34]. In addition, several species of hymenopteran parasitoids such as Apanteles sp., Dolichogenidea metesae (Nixon), Brachymeria carinata Joseph, Goryphus bunoh Gauld, Pediobius anomalus (Gahan), Apanteles aluella (Sumatra), Cotesia sp. and Glypapanteles sp.; as well as predators such as Callimerus arcufer Chapin (Coleoptera: Cleridae) and Cosmolestes picticeps Stål (Hemiptera: Reduviidae) reportedly attack the bagworms in Malaysia [35], indicating a high potential of their use in biological control of the devastating oil palm pest. However, further research is needed to develop efficient protocols for the mass production of these natural enemies. The success of using these natural enemies against the bagworms will also require addressing other bottlenecks such as changing the attitudes of farmers who prefer chemical insecticides for their fast action and effectiveness, despite their hazardous impacts on human and environmental health. The effectiveness of the biocontrol agents against the bagworms may also be hampered by hyperparasitism, e.g., Pediobius imbreus (Walker) (Hymenoptera: Eulophidae) against D. metasae [35] and their susceptibility to chemical insecticides [34], among other factors.

2.1.3. Other Defoliating Lepidopterans

Females of the palm moth Stenoma impressella Busck (Lepidoptera: Elachistidae) lay eggs on the adaxial frond surfaces [9]. Early feeding by S. impressella larvae damages the abaxial frond surface, except for secondary veins. In later feeding, the entire leaf tissue, except for midveins, is consumed. Rhysipolis sp. (Hymenoptera: Braconidae) was identified as the most important natural enemy of S. impressella in South America, but the rate of parasitism is only 7–18%. Synthetic chemicals, e.g., teflubenzuron, chlorantraniliprole and flubendiamide cause 95–100% mortality of S. impressella in oil palm plantations [9][36][37].
The palm king Amathusia phidippus (L.) (Lepidoptera: Satyrinae) is a common defoliator of oil palm in Southeast Asia [9]. The eggs are laid in a row, where larvae hatch in 6–7 days and voraciously feed on the underside of the leaf, from the tip towards the base. The larvae are greenish-grey to brown with longitudinal bands and a thick pile of reddish- setae, tufts of longer setae on the second and third abdominal segments, paired hornlike processes on the head and paired processes projecting from the anal segment. Chalcidoid wasps appear to be important parasitoids of A. phidippus [9].
The split-banded owlet Opsiphanes cassina Felder (Lepidoptera: Nymphalidae) is an important pest of oil palm in Central America, Colombia, Ecuador and Peru [38]. A natural enemy complex of hymenopterous parasitoids and a nuclear polyhedrosis disease apparently regulate populations of O. cassina. Its larval populations have been controlled by applications of carbaryl. Although the control of adults with insecticide-laced honey baits is reportedly effective against O. cassina, the technique could be hazardous to many kinds of non-target organisms [38]. The larva of another nymphalid species, Opsiphanes invirae Hübner has a bright green body marked by two thin longitudinal stripes of yellow-ochre, a pink head with two pointed extensions facing backward, and the last abdominal segment ending in a long, bifid and coniform tail [39]. In Brazil, the mass production of the parasitoid wasp Palmistichus elaeisis Delvare & LaSalle (Hymenoptera: Eulophidae) from alternative hosts has allowed inundative biological control of O. invirae populations in oil palm crops [40].

2.1.4. Leaf Beetles

Leaf beetles (Coleoptera: Chrysomelidae), with 37,000 described species and possibly up to 23,000 more to be described, are the third largest family in the order Coleoptera after Curculionidae and Staphylinidae [41]. Chrysomelids are small to medium-sized beetles, often brightly colored, boldly patterned, or metallic, with hairs or scales in some species. Several species of leaf beetles attack oil palms in different parts of the world and are controlled using different methods. The entomopathogenic fungus Metarhizium sp. was used to control Alurnus humeralis Rosenberg in Ecuador [42]. Dense populations of C. vagelineata have been observed to diminish after heavy rains [38][43]. Barrios et al. [43] found field-collected C. vagelineata to be infected by Lecanicillium lecanii and Metarhizium anisopliae, which could be developed into biopesticides against the pest.

2.1.5. Grasshoppers

Segestidea novaeguineae (Brancsik), Segestidea defoliaria Uvarok and Segestes decoratus Redtenbacher (Orthoptera: Tettigoniidae) are pests of oil palm in Papua New Guinea [9]. Meanwhile, Valanga nigricornis Burmeister (Orthoptera: Acrididae), Sexava nubila and S. coriacea (Orthoptera: Tettigoniidae) were reported as pests of oil palm in Indonesia [44]. Grasshoppers often attack the younger fronds first, but dense populations can effectively defoliate the entire palm. Often, their damage is noticed before the insects themselves are seen [9]. The nymphs and adults of endoparasite Stichotrema dallatorreanum Hofeneder (Strepsiptera: Myrmecolacidae) are potential classical biocontrol agents against these grasshoppers [45].

2.2. Fruit Scrapers

The oil palm fruit scraper, Demotispa neivai Bondar (Coleoptera: Chrysomelidae) is an important pest in commercial plantations and distributed in Central and South American countries [46]. Adults of D. neivai are reddish-brown, oval-shaped, dorsally flattened, and convex laterally [10]. Adults damage oil palm fruits, with a consumption rate of 12.35 mm2 d−1 per adult on exocarp [46]. The scrapping by D. neivai feeding on the exocarp causes a gray corky appearance. The resultant drying of fruits affects palm oil production. The use of natural plant extracts such as Ricinus communis L., Citrus sinensis Oesbek, Nicotiana tabacum L., and Capsicum annuum L. are a valuable tool for controlling D. neivai [47]. Moreover, entomopathogenic fungal isolates of B. bassiana and M. anisopliae are effective against D. neivai with the potential to be used as biological control agents, hence reducing reliance on hazardous chemical insecticides [48].

2.3. Sap Feeders

Prominent oil palm sap feeders are true bugs (Heteroptera) in the families Miridae and Tingidae [9]. For instance, the spindle bug Carvalhoia arecae Miller and China (Hemiptera: Miridae) attacks young oil palms in nurseries [49][50]. Inorganic insecticides such as malathion 5% dust, phorate 10% granules, monocrotophos 0.15% spray, and lambda cyhalothrin 0.10% are effective in controlling the pest [51].
Among tingids, the lace bug Stephanitis typica (Distant) is the best-known sapsucker associated with palms in Asia through to New Guinea [9]. Females typically lay eggs concealed in a lipid substance and insert them deep in the abaxial surfaces of fronds. Nymphs hatch after about 12 days. Stephanitis typica populations surge during dry periods. Stylets are inserted through the stomata, rupturing cell walls and terminating in the phloem [52]. Nymphs and adults feed on the lower surfaces of leaves, causing whitish-to-yellowish spots on the corresponding upper leaf surfaces. The feeding on the lower leaf surfaces leaves dark brown or black marks. Chemical insecticides are commonly used to control outbreaks of S. typica, but their effectiveness is questionable [9]. Stethoconus praefectus (Distant) (Hemiptera: Miridae) an obligate predator, and, two egg parasitoids namely Erythmelus panis and Anagrus sp. (Hymenoptera: Mymaridae) have been reported as natural enemies of S. typica in India [53].
Another notable tingid associated with oil palm is Leptopharsa gibbicarina Froeschner [9]. It is also the main vector of the Pestalotiopsis fungal complex in oil palm in the Americas [19]. The females insert their eggs into leaf tissue along a major vein of the abaxial surface, usually covering them with excrement. Upon hatching, larvae mingle with the adults, maturing in 6 weeks. The adults live for more than a month. They are relatively more abundant in the dry season [54]. The bugs prefer upper and middle fronds, rarely attacking the older fronds. Leaf surfaces injured by lace bug feeding may be an entry point for pathogenic fungi, such as Pestalotiopsis spp. Natural enemies of L. gibbicarina include Neuroptera, ants (especially Crematogaster spp.) and B. bassiana [55]. When these are not effective in maintaining low populations of the lacebug, an option is to treat the palm with a systemic insecticide [9]. Martínez et al. [19] reported that novaluron, teflubenzuron, and triflumuron are highly effective against L. gibbicarina.
Besides insects, at least 31 species of tetranychid mites suck sap from palms [9]. For instance, Retracrus elaeis Keifer (Acari: Eryophidae), feeds on the abaxial frond surfaces of oil palms in tropical America [54]. This mite has been associated with severe yellowing of palm leaves. Foliar spraying with sulfur reduces its severity [56]. Another mite recorded on oil palm foliage in the American tropics is the red spider mite Tetranychus mexicanus (McGregor) (Acari: Tetranychidae), but its damage is minimal [9].

2.4. Borers

A palm borer makes a tunnel by chewing or burrowing into the stem, crown, unopened inflorescences, flowers, fruits, peduncles, petioles, fronds or roots of the palm tree. The major oil palm borers belong to orders Isoptera, Coleoptera and Lepidoptera [57].

2.4.1. Palm Weevils

Among the coleopterans, weevils (Curculionidae) are characterized by an elongated rostrum or snout with mandibles at the distal end for chewing host tissue or excavating oviposition sites [58]. The larvae, which are the most destructive stage, are protected from most predators, parasites and external abiotic factors as they cryptically feed inside the host tissues. The success of palm weevil borers may be due to their specialization as borers within the Arecaceae and sometimes including other monocotyledons, such as sugarcane (Poaceae), banana (Musaceae) and pineapple (Bromeliaceae) [57]. Palm weevil borers fall into seven subfamilies: Dryophthorinae (Rhynchophorinae), Cholinae, Baridinae, Erirhininae, Petalochilinae, Scolytinae and Platypodinae. In particular, palm-associated members of the Rhynchophorinae are the most damaging to palms worldwide. Four tribes within the Rhynchophorinae, i.e., Rhynchophorini, Sphenophorini, Diocalandrini and Orthognathini are the major borers of palms in general [57].
Species in the weevil genera Rhynchophorus and Dynamis are most often referred to as ‘palm weevils’ and are relatively large insects, with adult length and width ranging from 3.5 cm to 5 cm and 1 cm to 2 cm, respectively, while the larvae are approximately 3.5–6.4 cm long and 1–2.5 cm wide [57]. Adults of Dynamis species are usually glossy black, in contrast to Rhynchophorus species which can exist in varying colors [59]. Dynamis and Rhynchophorus lay between 30 and 832 eggs in about a 42-day oviposition period [59].
No species of Dynamis has been reported on oil palm. However, oil palm is attacked by Rhynchophorus palmarum, R. bilineatus, R. phoenicis, R. quadrangulus and R. ferrugineus [59][60][61][62][63][64][65]. The main pathway through which the weevils spread outside their native regions is the movement of infested palms [66]. Early signs of oil palm infestation by weevils include notches at the base of fronds with frass and pupal cocoons, eccentric crown growth, holes at the base of the cut palms and symptoms resembling those of drought stress, e.g., wilting and yellowing [67]. Cryptic larvae and adults that spend their entire life inside the palm tree may destroy the interior of the palm causing its collapse. Although visual inspection may allow early detection of signs of weevil attack on palms, palm infestation with Rhynchophorus is difficult to accurately detect prior to serious damage to the apical meristem. The females are attracted to and deposit eggs in palm sheaths and stems, where they lay eggs in damaged parts along the trunk or in petioles. Upon hatching, the apodal larvae begin feeding towards the interior of the palm and migrate towards the crown region where the larvae primarily develop while voraciously feeding on and irreparably destroying tissues in the trunk and subsequently leading to tree collapse [59]. About 20 larvae are needed to cause a lethal infestation. A delay in destroying the palms allows weevils to emerge and spread to other palm trees [57].
Rhynchophorini are highly devastating pests. For example, the Gulf region of the Middle East, which accounts for nearly 30% of global palm production, has been threatened by R. ferrugineus since the mid-1980s [68]. The economic burden due to the eradication of 1% and 5% of severely infested palms of 259,172 hectares was estimated to range from $5.18 to $25.92 million, respectively. Besides this, the indirect losses would increase several folds. Further, it is also estimated that savings due to the curative treatment of palms in the early stage of attack at the above infestation levels and hectarage range from $20.73 to $103.66 million, respectively [68]. Considering the above economic loss, it is important that countries where oil palm is grown strengthen the on-going management programmes against palm weevils.
The major components of integrated pest management (IPM) programme for palm weevil control include surveillance of the pest; maintaining plant and field sanitation; trapping adult weevils; preventive chemical treatment of wounds; filling the leaf axils of young palms with a mixture of insecticide and sand; curative chemical treatment of infested palms; and cutting and burning of severely infested palms [65]. Adult populations of palm weevils can be monitored by pheromone traps, acoustic detection or infra-red systems [8][64][67]. Abandoning oil palm fields over time makes them reservoirs for the weevils [69]. Flood irrigation causes dampness at the base of the palm and its offshoots, creating a favorable environment for the weevils to lay their eggs [70]. The chemicals used to control palm weevils include methidathion, oxydemeton-methyl, carbaryl, cypermethrin, deltamethrin dimethoate, chlorpyrifos, fipronil, imidacloprid and trichlorphon [71]. Post-application monitoring is required to confirm successful control of the weevils which is characterized by cessation of oozing of sap from weevil-damaged parts [67]. In regions with very high relative humidity, deeply damaged stems are treated by stem cleaning followed by filling these cavities with wet sand mixed with pesticide dust and the treated parts with a polyethylene sheet to retain humidity [71].
Early detection of Rhynchophorus weevil infestation followed by insecticide treatment may help palms to recover. However, palms in the latter stages of attack exhibit extensive tissue damage in the region of the apical meristem, often harboring several overlapping generations of the borers. These palms are difficult to treat, and they usually die. The lethal nature of this pest, coupled with the high value of the attacked palm species, warrants early action against the weevils [8].
Another weevil attacking bases of pruned oil palm fronds is Metamasius inaequalis (Gyllenhal) (Coleoptera: Curculionidae) [72]. Pitfall traps and palm tissue baited with aggregation pheromone and treated with insecticides are reportedly effective in controlling M. inaequalis [9]. Additionally, Temnoschoita quadrimaculata Gly. (Coleoptera: Curculionidae) is a borer of oil palms in nurseries and young plantations in Ghana [73]. Inflorescences of older palms can be severely damaged, leading to significant tunneling through both dead and living tissue near the point of entry. Damage includes premature withering of fronds and necrosis of the terminal shoot. Young palms can be killed by damage to the crown and apical meristem by the activity of T. quadrimaculata [57]. The base-borer weevil, Sparganobasis subcruciata Marshall (Coleoptera: Curculionidae: Dryopthorinae) is also a lethal pest of oil palm in Papua New Guinea and Indonesia [61][74]. Although S. subcruciata attacks the bases of only mature oil palms older than 10 years at low incidence, the affected trees harbor hundreds of the weevil larvae, resulting in massive damage of the internal basal stem tissue and subsequent tree collapse.

2.4.2. Rhinoceros Beetles

Another destructive oil palm borer is the rhinoceros beetle Oryctes rhinoceros (L.) (Coleoptera: Scarabaeidae). The female lays up to 512 eggs in rotting stumps and rubbish piles. The eggs hatch in 8–12 days into white grubs taking 12–200 days to turn into pupae and then adults which can have a longevity of 100–270 days [75]. Young adults of O. rhinoceros bore and damage the crowns of healthy palms, penetrating 10–50 cm towards the center of the spear cluster and feeding on juice from host tissue. The major sign of palm infestation by O. rhinoceros is crushed tissue pushed out of the entrance of the burrow. The pest inflicts major damage to palms 1–3 years old (sometimes leading to death), while in healthy older palms the damage caused can be minor [57]. Field sanitation such as removal, burning, burial or destruction of dead standing palm logs, stumps and rubbish piles which are breeding sites for the beetles are helpful in managing the pest [76]. Although insecticides such as lambdacyhalothrin, cypermethrin, fenvelarate and chlorpyrifos are commonly used against O. rhinoceros, their effectiveness is limited due to the cryptic nature of the beetles inside the plant tissue [76]. A male-produced aggregation pheromone, ethyl-4-methyloctanoate [77], is widely used in mass trapping, monitoring and augmentation with biopesticides [78][79]. The use of biological control agents associated with O. rhinoceros is immense, including predators, parasitoids and entomopathogenic fungi, bacteria, and nematodes, but only a few biopesticides products are available in the market [76][80]. These reports highlight Rhabdionvirus oryctes as a landmark success story of classical biological control of O. rhinoceros. Similarly, several fungal-based biopesticides such as M. anisopliae and Beauveria brogniartii (Sacc.) Petch, and entomopathogenic nematodes such as Heterorhabditis sp. are marketed for the control of O. rhinoceros [80]. However, the bulk of reports on natural enemies of O. rhinoceros are largely about their identification and efficacy bioassays under controlled conditions, but with limited commercial field application. For biopesticide products in the market, their potency may last long and are relatively easier and less costly to apply compared to chemical pesticides, but their scarcity raises their costs way above that of conventional pesticides [79].
The rhinoceros beetle, Strategus aloeus L. is a pest in oil palm plantations in the Americas. During the replanting of old palm trees by new palms, adult S. aloeus colonize palm trees. Adults attack young palms by tunneling into the soil near the palm trees, boring their way into the meristem of the plant. The collection of the immature stages on dead palms [81] and chemical insecticides are the main methods of controlling S. aloeus [82].

2.4.3. Lepidopteran Borers

Aside from coleopterans, Cyparissius daedalus (Cramer) (Lepidoptera: Castniidae) is a major borer of oil palm in northern South America and the Amazon basin [9]. Each female lays about 265 eggs, and it takes about 17 days for larvae to hatch. The larval stage, consisting of 14 instars, takes up to 1 year and the pupal stage lasts about 35 days. The early instars bore into the fruits and peduncles of oil palm causing rotting of the affected parts. Later instars make shallow galleries between the petioles and the stem, causing premature frond abscission. In a few cases, palm death occurs when larvae bore the growing point of the palm. Oil palm becomes susceptible at about 5 years after planting. An egg parasitoid, Ooencyrtus sp. (Hymenoptera: Encyrtidae), was isolated from eggs of C. daedalus in Peru, where it occasionally regulates its populations. Scouting plantations, pruning and destroying infested fronds and rotten fruit stalks are considered to be good preventive measures against C. daedalus.
Sagalassa valida Walker (Lepidoptera: Brachodidae) is a small, brown-banded moth, whose larvae cause significant damage to the roots of young oil palms causing up to 70% yield losses [18][57]. The larvae consume the entire central core of the infested quaternary and tertiary roots, starting from their apex. The short-lived adults move between surrounding forests and oil palm crops; hence, the greatest damage is at the forest-plantation borders [83]. Insecticide application is recommended for infestation levels, where 20% of the primary roots are attacked [14]. Cultural control methods involve keeping and maintaining clean borders between the plantation and the surrounding forest [57]. Mulching with empty bunches prevents the caterpillar from getting into the roots [14]. Biological control with the entomopathogenic nematode Steinernema carpocapsae is reportedly effective against S. valida in the laboratory and field trials [57], but reports of its practical use in managing the pest are scarce. The presence of the predatory ant Pachycondyla harpax (Fabricius) (Hymenoptera, Formicidae) reduces infestation by S. valida [14].
The African spear borer Pimelephila ghesquierei (Tams) (Lepidoptera: Crambidae) is a pest of oil palm in West Africa [9]. Two or three neonates penetrate the leaflets of the growing, unopened spears, forming galleries and mostly destroying the bases of young palms [52]. The caterpillars hatch from eggs laid at the base of the spear leaf and bore into it. The fronds may break off where the rachis has been weakened. Damage by P. ghesquierei greatly impacts young palms in nurseries or in recent field plantings [31]. Collection and destruction of pupae have been recommended to prevent population build-up in nurseries or young plantations [31]. The pest mostly attacks stressed and/or shaded palms [31].

References

  1. Murphy, D.J.; Goggin, K.; Paterson, R.R.M. Oil palm in the 2020s and beyond: Challenges and solutions. CABI Agric. Biosci. 2021, 2, 39.
  2. Ritchie, H.; Roser, M. Forests and Deforestation. Available online: https://ourworldindata.org/forests-and-deforestation (accessed on 30 June 2022).
  3. Kuepper, B.; Drost, S.; Piotrowski, M. Latin American Palm Oil Linked to Social Risks, Local Deforestation; Chain Reaction Research: Washington, DC, USA, 2021.
  4. Obahiagbon, F.I. A review: Aspects of the African oil Palm (Elaeis guineesis Jacq.) and the implications of its bioactives in human health. Am. J. Biochem. Mol. Biol. 2012, 2, 106–119.
  5. Pirker, J.; Mosnier, A.; Kraxner, F.; Havlík, P.; Obersteiner, M. What are the limits to oil palm expansion? Glob. Environ. Change 2016, 40, 73–81.
  6. Woittiez, L.S.; Van Wijk, M.T.; Slingerland, M.; Van Noordwijk, M.; Giller, K.E. Yield gaps in oil palm: A quantitative review of ontributing factors. Eur. J. Agron. 2017, 83, 57–77.
  7. de Oliveira, T.A.; Martins, I.C.F.; Silva, J.G.; Lemos, W.P. Oil palm age and genotype interfere with defoliator lepidopteran infestation. Arq. Inst. Biol. 2021, 88, e00472020.
  8. Giblin-Davis, R.M.; Faleiro, J.R.; Jacas, J.A.; Pena, J.E.; Vidyasagar, P. Biology and management of the red palm weevil, Rhynchophorus ferrugineus. In Potential Invasive Pests of Agricultural Crops; Pena, J., Ed.; CAB International: Wallingford, UK, 2013; pp. 1–34.
  9. Howard, F.; Moore, D.; Giblin-Davis, R.; Abad, R. Insects on Palms, 1st ed.; CABI Publishing: Oxon, UK, 2001.
  10. Martínez, L.C.; Plata-Rueda, A.; Zanuncio, J.C.; Serrao, J.E. Leucothyreus femoratus (Coleoptera: Scarabaeidae): Feeding and behavioral activities as an oil palm defoliator. Fla. Entomol. 2013, 96, 55–63.
  11. Martínez, L.C.; Plata-Rueda, A.; Zanuncio, J.C.; Serrão, J.E. Life history traits and damage potential of an invasive pest Acharia fusca (Lepidoptera: Limacodidae) on oil palm. Ann. Entomol. Soc. Am. 2014, 107, 1086–1093.
  12. Kok, C.C.; Eng, O.; Razak, A.R.; Arshad, A.M. Microstructure and life cycle of Metisa plana Walker (Lepidoptera: Psychidae). J. Sustain. Sci. Manag. 2011, 6, 51–59.
  13. Saravanan, L.; Kalidas, P.; Phanikumar, T.; Dwarakakumar, D.; Gupta, A.; Arunkumar, R. Life history, phenology, host range and natural enemies of Acria meyricki Shashank and Ramamurthy (Lepidoptera: Depressariidae): An emerging defoliator of oil palm, Elaeis guineenis Jacq. In India. Phytoparasitica 2020, 48, 427–454.
  14. Corley, R.H.V.; Tinker, P.B.H. The Oil Palm, 5th ed.; Wiley-Blackwell: West Sussex, UK, 2016; 626p, ISBN 9781405189392.
  15. Martínez, L.C.; Plata-Rueda, A. Lepidoptera vectors of Pestalotiopsis fungal disease: First records in oil palm plantations from Colombia. Int. J. Trop. Insect Sci. 2013, 33, 239–246.
  16. Alvarado, H.; de La Torre, R.A.; Barrera, E.; Martínez, L.; Bustillo, A. Ciclo de vida y tasa de consumo de Euprosterna elaeasa Dyar (Lepidoptera: Limacodidae) defoliador de la palma de aceite. Rev. Palmas 2014, 35, 41–51.
  17. Martínez, L.C.; Hurtado, R.; Araque, L.; Rincón, V. Avances de la campaña regional para el manejo de la información de insectos defoliadores en la zona central. Palmas 2009, 30, 51–61.
  18. Hernández-Lambraño, R.; Caballero-Gallardo, K.; Olivero-Verbel, J. Toxicity and antifeedant activity of essential oils from three aromatic plants grown in Colombia against Euprosterna elaeasa and Acharia fusca (Lepidoptera: Limacodidae). Asian Pac. J. Trop. Biomed. 2014, 4, 695–700.
  19. Martínez, L.C.; Plata-Rueda, A.; Serrão, J.E. Effect of benzoylphenyl ureas on survival and reproduction of the lace bug, Leptopharsa gibbicarina. Insects 2021, 12, 34.
  20. Zeddam, J.L.; Cruzado, J.A.; Rodriguez, J.L.; Ravallec, M. A new nucleopolyhedrovirus from the oil-palm leaf-eater Euprosterna elaeasa (Lepidoptera: Limacodidae): Preliminary characterization and field assessment in Peruvian plantation. Agric. Ecosyst. Environ. 2003, 96, 69–75.
  21. Martínez, L.C.; Plata-Rueda, A.; Serrão, J.E. Effects of insect growth regulators on mortality, survival, and feeding of Euprosterna elaeasa. Agronomy 2021, 11, 2002.
  22. Rhainds, M.; Davis, D.R.; Price, P.W. Bionomics of bagworms (Lepidoptera: Psychidae). Annu. Rev. Entomol. 2009, 54, 209–226.
  23. Rozziansha, T.A.P.; Priwiratama, H.; Susanto, A. Existing and emerging bagworms in oil palm plantation in Indonesia. In Proceedings of the Fourth IOPRI-MPOB International Seminar: Existing and Emerging Pests and Diseases of Oil Palm Advances in Research and Management, Bandung, Indonesia, 13–14 December 2012.
  24. Murgianto, F.; Edyson, E.; Setyawan, Y.P.; Tamba, L.M.; Ardiyanto, A.; Siregar, A.H. First report of an ice cream cone bagworm Manatha conglacia Haettenschwiler (Lepidoptera: Psychidae) in oil palm plantations of Central Kalimantan, Indonesia. In Proceedings of the International Conference on Tropical Agrifood, Feed and Fuel (ICTAFF 2021), Virtual, 7 January 2022.
  25. Hisham, N.B. Study of Duration Larvae Stage Bagworm (Lepidoptera: Psychidae) on Michelia champaca Trees In Ex-Situ and In-Situ Rearing and Its Species Identification. Bachelor’s Thesis, University Malaysia, Kota Samarahan, Sarawak, Malaysia, 2012.
  26. Leong, T.M.; Lim, K.K.P. Record of the bagworm moth, Mahasena corbetti Tams in Singapore (Lepidoptera: Psychidae). NiS 2012, 5, 1–5.
  27. Firake, D.M.; Behere, G.T.; Arnscheid, W.R.; Kumar, R.; Ngachan, S.V. First report of coconut case caterpillar, Mahasena corbetti Tams (Lepidoptera: Psychidae) from India. Phytoparasitica 2018, 46, 355–364.
  28. Batugal, P.V.; Rao, R.; Oliver, J. (Eds.) Coconut Genetic Resources; International Plant Resources Genetic Institute-Regional Office for Asia; The Pacific and Oceania (IPGRI-APO): Sardang, Selangor DE, Malaysia, 2005.
  29. Rahman, M.A.; Jahan, H.; Talukdar, S.; Kazi1, R. First Record of the Bagworm Moth, Mahasena corbetti Tams (Lepidoptera: Psychidae) in Bangladesh. Int. J. Innov. Res. 2019, 4, 22–26.
  30. Yew Cheong, L.; Chin Chong, T. Understanding pest biology and behaviour for effective control of oil palm bagworm. Planter 2012, 88, 669–715.
  31. Howard, F.W.; Abad, R.G. Lepidoptera. In Insects on Palms; Howard, F.W., Moore, D., Giblin-Davis, R.M., Abad, R., Eds.; CABI Publishing: Oxon, UK, 2001.
  32. Basri, W.M.; Ramlah, A.A.S.; Norman, K. Status report on the use of Bacillus thuringiensis in the control of some oil palm pests. Elaeis 1994, 6, 82–101.
  33. Priwiratama, H.; Rozziansha, T.A.P.; Susanto, A.; Prasetyo, A.E. Effect of bagworm Pteroma pendula Joannis attack on the decrease in oil palm productivity. J. Hama Penyakit Tumbuh. Trop. 2019, 19, 101–108.
  34. Mazuan, S.; Mohamed, S.; Ishak, I.; Omar, D.; Asib, N. Optimization of motorized backpack mistblower for efficient application of insecticides against the bagworm. Pak. J. Agric. Sci. 2001, 34, 479–485.
  35. Cheong, Y.L.; Sajap, A.S.; Hafidzi, M.N.; Omar, D.; Abood, F. Outbreaks of bagworms and their natural enemies in an oil palm, Elaeis guineensis, plantation at Hutan Melintang, Perak, Malaysia. J. Entomol. 2010, 7, 141–151.
  36. Aldana de la Torre, R.C.; Aldana, J.; Calvache, H.; Franco, P. Manual de Plagas de la Palma de Aceite en Colombia, 4th ed.; Cenipalma: Bogota, Colombia, 2010.
  37. Barrios, C.; Aldana-De La Torre, R.C.; Bustillo-Pardey, A. Biología del defoliador de la palma de aceite, Stenoma cecropia Meyrick (Lepidoptera: Elachistidae). Palmas 2013, 34, 13–19.
  38. Genty, P.; Desmier de Chenon, R.; Morin, J.P. Ravageurs du palmier à huile en Amérique latine—Las plagas de la palma aceitera en America Latina—Oil palm pests in Latin America. Oléagineux 1978, 33, 325–417.
  39. de Sousa Brandão, A.D.; Farias, P.R.S.; Dionisio, L.F.S.; Tinôco, R.S.; da Silva, A.G.; da Silva, T.A.F. Spatial and temporal distribution of Opsiphanes invirae (Lepidoptera: Nymphalidae) in oil palm, Pará State, Brazil. Rev. Bras. Cienc. Agrar. 2017, 12, 464–469.
  40. Morais, W.D.C.; Plata-Rueda, A.; Martínez, L.C.; Zanuncio, A.J.V.; Fernandes, F.L.; Wilcken, C.F.; Zanuncio, J.C.; Serrão, J.E. Potential of Diaphania hyalinata and Tenebrio molitor as alternative host for mass rearing of Palmistichus elaeisis (Hymenoptera: Eulophidae). Entomol. Gen. 2019, 39, 285–294.
  41. Flower, R.W. Leaf beetles (Coleoptera: Chrysomelidae). In Encyclopedia of Entomology; Springer: Dordrecht, The Netherlands, 2004.
  42. Castillo Carrillo, C.I. Biodiversity in Ecuador and its immense potential for agricultural pest control. In Agricultural, Forestry and Bioindustry Biotechnology and Biodiscovery; Springer: Cham, Switzerland, 2020; pp. 143–161.
  43. Barrios, C.; Castillo, N.; Bustillo, A.; Méndez, A. Biología del raspador de la flecha, Cephaloleia vagelineata Pic. (Coleoptera: Chrysomelidae), plaga de la palma de aceite en Colombia. Palmas 2018, 39, 59–65.
  44. Desmier de Chenon, R.; Sudharo, P.; Poelongan, Z.H. Nettle caterpillars and grasshoppers of oil palm in Indonesia. In Proceedings of the International Conference on Pests and Diseases of Importance to the Oil Palm Industry, Kuala Lumpur, Malaysia, 18–19 May 2004; pp. 75–95.
  45. Kathirithamby, J.; Solulu, T.; Caudwell, R. Descriptions of female Myrmecolacidae (Strepsiptera) parasitic in Orthoptera (Tettigoniidae) in Papua New Guinea. Tijdschr. Entomol. 2001, 144, 187–196.
  46. Martínez, L.C.; Plata-Rueda, A. Biological aspects and food consumption of fruit scraper of oil palm, Demotispa neivai (Coleoptera: Chrysomelidae). J. Oil Palm Res. 2014, 26, 47–53.
  47. Martínez, L.C.; Plata-Rueda, A.; Zanuncio, J.C.; Serrão, J.E. Bioactivity of six plant extracts on adults of Demotispa neivai (Coleoptera: Chrysomelidae). J. Insect Sci. 2015, 15, 34.
  48. Martínez, L.C.; Plata-Rueda, A.; Ramírez, A.; Serrão, J.E. Susceptibility of Demotispa neivai (Coleoptera: Chrysomelidae) to Beauveria bassiana and Metarhizium anisopliae entomopathogenic fungal isolates. Pest Manag. Sci. 2022, 78, 123–133.
  49. Yeshwanth, H.M.; Prathapan, K.D. First report of the occurrence of the arecanut spindle bug, Mircarvalhoia arecae (Miller & China) in the Andaman and Nicobar Islands. J. Trop. Agric. 2014, 52, 82–84.
  50. Kantharaju, N.C.; Venkatesh, H.; Yalavar, S. Biology of arecanut spindle bug, Carvalhoia arecae Miller and China (Heteroptera: Miridae). J. Ecol. Environ. 2011, 29, 148–151.
  51. Kantharaju, N.; Thippeswamy, C.; Venkatesh, H. Efficacy of certain insecticides against arecanut spindle bug, Carvalhoia arecae Miller and China (Heteroptera: Miridae) under field conditions. Int. J. Plant Prot. 2009, 2, 237–239.
  52. CABI. Invasive Species Compendium. Available online: www.cabi.org/isc (accessed on 5 June 2022).
  53. Poorani, J.; Padmanaban, B.; Thanigairaj, R. Natural enemies of banana lacewing bug, Stephanitis typica (Distant) in India, including first report of Anagrus sp. (Hymenoptera: Mymaridae) as its egg parasitoid. Mun. Ent. Zool. 2019, 14, 83–87.
  54. Zenner de Polanía, I.; Posada Flórez, F.J. Manejo de Insectos, Plagas y Benéficos, de la Palma Africana; Manuel de Asistencia Técnica No. 54; Instituto Colombiano Agropecuario: Santa Fé de Bogotá, Colombia, 1992.
  55. Aldana de la Torre, J.; Calvache Guerrero, H.; Méndez, A. Distribución de hormigas y su efecto sobre Leptopharsa gibbicarina en una plantación de palma de aceite. Palmas 1995, 16, 19–23.
  56. Ramos, Y.P.; Ibagué, D.F.; Arias, N.A.A.; Alzate, O. Relación entre el anaranjamiento foliar y la presencia del ácaro de fronde (Retracrus elaeis) y su manejo con aspersiones de azufre en el cultivo de palma de aceite (Elaeis guineensis Jacq.). Palmas 2019, 40, 161–169.
  57. Giblin-Davis, R. Borers. In Insects on Palms; Howard, F.W., Moore, D., Giblin-Davis, R.M., Abad, R., Eds.; CABI Publishing: Oxon, UK, 2001.
  58. Matsumura, Y.; Jafarpour, M.; Reut, M.; Shams Moattar, B.; Darvizeh, A.; Gorb, S.N.; Rajabi, H. Excavation mechanics of the elongated female rostrum of the acorn weevil Curculio glandium (Coleoptera; Curculionidae). Appl. Phys. A 2021, 127, 348.
  59. Wattanapongsiri, A. A revision of the Genera Rhynchophorus and Dynamis (Coleoptera: Curculionidae). Ph.D. Thesis, Oregon State University, Corvallis, OR, USA, 1996.
  60. Hallett, R.H.; Crespi, B.J.; Borden, J. Synonymy of Rhynchophorus ferrugineus (Olivier) 1790 and R. vulneratus (Panzer) 1798 (Coleoptera, Curculionidae, Rhynchophorinae). J. Nat. Hist. 2004, 38, 2863–2882.
  61. Priwiratama, H.; Prasetyo, A.E.; Pradana, M.G.; Rozziansha, T.A.P.; Susanto, A.; Desmier de Chenon, P. Weevil stem borer and mesocarp-eating beetle: New threat to oil palm plantations in Indonesia. In Proceedings of the PIPOC International Palm Oil Congress, Kuala Lumpur, Malaysia, 9–21 November 2019; pp. 67–81.
  62. Fiaboe, K.K.M.; Peterson, A.T.; Kairo, M.T.K.; Roda, A.L. Predicting the potential worldwide distribution of the red palm weevil Rhynchophorus ferrugineus (Olivier) (Coleoptera: Curculionidae) using ecological niche modeling. Fla. Entomol. 2012, 95, 659–673.
  63. Baguma, J.; Otema, M.; Ddamulira, G.; Naluyimba, R.; Egonyu, J.P. Distribution and incidence of the oil palm weevil Rhynchophorus phoenicis (Fabricius, 1801) (Coleoptera: Curculionidae) in selected agro-ecological zones of Uganda. Afr. Entomol. 2019, 27, 477–487.
  64. Egonyu, J.P.; Gitonga, K.J.; Khamis, F.M.; Copeland, R.S.; Finyange, P.; Odhiambo, R.; Ddamulira, G. Trapping, identification and rearing of edible palm weevils in Kenya and Uganda. J. Insects Food Feed 2021, 7, 1243–1253.
  65. Faleiro, R.J.; Al-Dandan, A.M.; Raikar, S.P.; Abdallah, A.B.; Al-Abdullah, A.L.; Gadi, I. Attract and kill technology to control Red palm weevil: Experiences on date palm in Saudi Arabia and oil palm in India. In Proceedings of the 2nd Date’s Festival, Siwa Oasis, Egypt, 27–29 October 2016.
  66. Cabello, T. Biology and population dynamics of the Red palm weevil, Rhynchophorus ferrugineus (Olivier, 1790) (Coleoptera: Dryophthoridae) in Spain. In I Jornada Internacional sobre el Picudo Rojo de las Palmeras; Fundación Agrolimed, Generalitat Valenciana: Valencia, Spain, 2007; pp. 12–13.
  67. Abraham, V.A.; Al-Shuaib, M.A.; Falleiro, J.R.; Abozuhairah, R.A.; Vidyasagar, P.S.P.V. An integrated management approach for the red palm weevil Rhynchophorus ferrugineus Oliv. A key pest of date palm in the Middle East. J. Sci. Res. Agric. Sci. 1998, 3, 77–84.
  68. El-Sabea, A.M.R.; Faleiro, J.R.; Abo-El-Saad, M.M. The threat of red palm weevil Rhynchophorus ferrugineus to date plantations of the Gulf region in the Middle-East: An economic perspective. Outlooks Pest Manag. 2009, 20, 131.
  69. Abozuhairah, R.A.; Vidyasagar, P.S.P.V.; Abraham, V. Integrated management of red palm weevil Rhynchophorus ferrugineus in date palm plantations of the Kingdom of Saudi Arabia. In Proceedings of the International Congress of Entomology, Florence, Italy, 25–31 August 1996; pp. 25–36.
  70. Aldryhim, Y.; Al-Bukiri, S. Effect of irrigation on within-grove distribution of red palm weevil Rhynchophorus ferrugineus. J. Agric. Mar. Sci. 2003, 8, 47–49.
  71. Vidyasagar, P.S.P.V.; Al-Saihati, A.A.; Al-Mohanna, O.E.; Subbei, A.I.; Abdul Mohsin, A.M. Management of red palm weevil Rhynchophorus ferrugineus Olivier. A serious pest of date palm in Al-Qatif, Kingdom of Saudi Arabia. Plant. Crops 2000, 28, 35–43.
  72. Giblin-Davis, R.M.; Oehlschlager, A.C.; Perez, A.; Gries, G.; Gries, R.; Weissling, T.J.; Chinchilla, C.M.; Peña, J.E.; Hallett, R.H.; Pierce, H.D.; et al. Chemical and behavioral ecology of palm weevils (Curculionidae: Rhynchophorinae). Fla. Entomol. 1996, 9, 153–167.
  73. Asante, S.K.; Kumar, R.A.D. Distribution and abundance of Temnoschoita quadrimaculata Gly (Coleoptera: Curculionidae) on oil palm, Elaeis guineensis Jacq. in Ghana. Insect Sci. Appl. 1987, 8, 115–120.
  74. Dewhurst, C.F.; Pilotti, C.A. First record of the base-borer weevil, Sparganobasis subcruciata Marshall (Coleoptera: Curculionidae: Dryopthorinae), from oil palm (‘Elaeis guineensis’ Jacq.) in Papua New Guinea and its association with decaying stem tissue. Aust. Entomol. 2012, 39, 197–207.
  75. Alouw, J.C.; Hosang, M.L.; Nguyen, Q. Biotechnology contributing to integrated pest management: The example of two major coconut pests, Oryctes rhinoceros and Brontispa longissima. In Coconut Biotechnology: Towards the Sustainability of the ‘Tree of Life’; Adkins, S., Foale, M., Bourdeix, R., Nguyen, Q., Biddle, J., Eds.; Springe: Cham, Switzerland, 2020; pp. 151–168.
  76. Manjeri, G.; Muhamad, R.; Tan, S.G. Oryctes rhinoceros beetles, an oil palm pest in Malaysia. Annu. Res. Rev. Biol. 2014, 4, 3429–3439.
  77. Hallett, R.H.; Perez, A.L.; Gries, G.; Gries, R.; Pierce, H.D.; Yue, J.; Oehlschlager, A.C.; Gonzalez, L.M.; Borden, J.H. Aggregation pheromone of coconut rhinoceros beetle, Oryctes rhinoceros (L.) (Coleoptera: Scarabaeidae). J. Chem. Ecol. 1995, 95, 1549–1570.
  78. Chakravarthy, A.K.; Chandrashekharaiah, M.; Kandakoor, S.B.; Nagaraj, D.N. Efficacy of aggregation pheromone in trapping red palm weevil (Rhynchophorus ferrugineus Olivier) and rhinoceros beetle (Oryctes rhinoceros Linn.) from infested coconut palms. J. Environ. Biol. 2014, 35, 479–484.
  79. Nordin, A.B.A.; Simeh, M.A.; Amiruddin, M.N.; Weng, C.K.; Salam, B.A. Economic feasibility of organic palm oil production in Malaysia. OPIEJ 2004, 4, 29–38.
  80. Paudel, S.; Mansfield, S.; Villamizar, L.F.; Jackson, T.A.; Marshall, S.D. Can biological control overcome the threat from newly invasive coconut rhinoceros beetle populations (Coleoptera: Scarabaeidae)? A review. Ann. Entomol. Soc. Am. 2021, 114, 247–256.
  81. Pallares, C.H.; de la Torre, J.A.A.; de Lucas, P.R.; Calvache, H.H.; Luque, J.E.; Correa, N. Análisis del comportamiento y comunicación química intraespecífica en Strategus aloeus (L.) (Coleoptera, Scarabaeidae-Dynastinae). Palmas 2000, 21, 185–194.
  82. Martínez, L.C.; Plata-Rueda, A.; Zanuncio, J.C.; Serrão, J.E. Comparative toxicity of six insecticides on the rhinoceros beetle (Coleoptera: Scarabaeidae). Fla. Entomol. 2014, 97, 1056–1062.
  83. Peña, E.A.; Jiménez, O.D. Distribución del daño del insecto Sagalassa valida Walker en el sistema radical de la palma de aceite (Elaeis guineensis Jacquin) en la zona de Tumaco. Palmas 1994, 15, 19–23.
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