The Featured Creatures collection provides in-depth profiles of insects, nematodes, arachnids, and other organisms relevant to Florida. These profiles are intended for the use of interested laypersons with some knowledge of biology as well as academic audiences. This publication profiles the destructive pest insect, Aonidiella orientalis, commonly called the “Oriental scale.” It includes the insect’s physical description, information about its range, its host plants, the damage it causes, and its economic importance. Integrated pest management strategies for control of this pest insect are included as well.
Introduction
The Oriental scale, Aonidiella orientalis (Newstead, 1894), belongs to the order Hemiptera, infraorder Coccomorpha and family Diaspididae (Miller and Davidson 2005). It is a highly polyphagous insect with a broad range of host plants and is widely distributed across 72 countries (García Morales et al. 2016). This insect may be found on the leaves, branches, trunks, shoots, and fruits of its hosts. Aonidiella orientalis is regarded as a serious pest in various regions of the world, causing significant economic losses to numerous important crops, including citrus, figs, mangoes, papayas, bananas, palms, tea, and some key ornamental plants, including Roystonea regia (royal palm), Dypsis spp. (e.g., areca palm, triangle palm), Phoenix spp. (date palms), Sabal spp. (e.g., cabbage palm), Hibiscus spp., Plumeria spp. (frangipani), and Ficus spp. (fig trees), among others, which are widely used in tropical and subtropical landscaping, including Florida (Dekle 1976; García Morales et al. 2016; European Food Safety Authority Panel on Plant Health 2022).
Description
Aonidiella orientalis is commonly found on leaves, fruits, stems, and the bases of palm fronds. This is a small insect, with females approximately 1.5–2.0 mm (~1/16 in) in diameter and males 1.0–1.3 mm (~1/32 in) long. The scale cover of the adult female is flat, circular to oval, and ranges in color from yellow to yellowish-brown. It often features a small, transparent or brown spot near the center called a subcentral exuvia (Figure 1).
Credit: Lyle Buss, UF/IFAS.
The cover of the second-instar female has the same texture and color as the adult female but is smaller with only one exuvia incorporated into the cover. Similarly, the cover of the immature male has the same color and texture but is smaller, with the first-instar exuvia located submarginally. The body of the adult female, as well as the eggs and first-instar nymphs (immatures called crawlers), are yellow (Miller and Davidson 2005; Watson and Kondo 2022). The body shape of the adult female (Figures 2 and 3) is somewhat inflated and marginally sclerotized with maturity but never reniform (kidney-shaped) (Watson 2002; Miller and Davidson 2005). This is a primary field diagnostic character differentiating A. orientalis from mature adult females of the other three species of the same genus known to occur in Florida: Aonidiella aurantii (Maskell, 1879), Aonidiella citrina (Coquillett, 1891), and Aonidiella taxus Leonardi, 1906.
Credit: Minor V. Solano Gutiérrez, UF/IFAS.
In slide-mounted specimens, the adult female can be distinguished from the other three species by her clusters of large ducts (macroducts) located near the sides of the back (dorsal submarginal area) on the first three abdominal segments before the pygidium (prepygidial abdominal segments I–III), and by the presence of small pores around the genital opening (perivulvar pores) (Miller and Davidson 2005; Watson and Kondo 2022).
Credit: a) Erin Powell, FDACS-DPI; b) Minor V. Solano Gutiérrez, UF/IFAS.
Distribution
Aonidiella orientalis is likely of East Asian origin. It was first described from Panicum sp. in India by Newstead in 1894 as Aspidiotus orientalis. It is a tropical and subtropical species, currently found in 72 countries (García Morales et al. 2016) (Figure 4). Its wide distribution is attributed to accidental spread through the human transport of infested plants and plant materials. It is also found in greenhouses in temperate regions (Watson 2002). In the United States, A. orientalis is known to be established only in Florida.
Credit: Minor V. Solano Gutiérrez, UF/IFAS, based on ScaleNet database.
Life Cycle and Biology
Aonidiella orientalis reproduces rapidly, with population densities peaking when developing between 15°C (59°F) and 30°C (86°F) (Badawi and Al-Ahmed 1990). As with other insects, its rate of development is temperature dependent. Females require an average of 44.2 days to develop from the crawler stage to the production of the first crawler at 25°C (77°F) (Elder and Smith 1995). Eggs hatch within 2–3 days at around 20°C (68°F) and within 7–9 hours at 30°C (86°F) (Watson and Kondo 2022). A single female can produce approximately 200 eggs during her lifetime (Waterhouse and Sands 2001). A. orientalis reproduces continuously throughout the year, with overlapping generations and all life stages coexisting in tropical conditions (Badawi and Al-Ahmed 1990).
Host Plants
Although Aonidiella orientalis is highly polyphagous, palms are the most common hosts in Florida. Worldwide, this scale occurs on host plants belonging to at least 189 genera in 77 families (García Morales et al. 2016). In Florida, from 2006 to 2025, 50% of Aonidiella orientalis reports were on coconut palm (Cocos nucifera) (FDACS-DPI Database 2025). Other common hosts in Florida include Roystonea regia (royal palm), Dypsis spp. (e.g., areca palm, triangle palm), Phoenix spp. (date palms), Sabal spp. (e.g., cabbage palm), and other ornamental plants like Hibiscus spp., Plumeria spp. (frangipani), and Ficus spp. (fig trees) (Dekle 1976; García Morales et al. 2016).
Credit: Adam Dale, UF/IFAS.
Damage and Economic Importance
Like other armored scales, Aonidiella orientalis uses its piercing-sucking mouthparts to feed on individual mesophyll parenchyma cells within leaves, fruits, or stems. Since mesophyll contains many chloroplasts, which are the primary sites of photosynthesis in plants, heavy infestations can lead to chlorosis (yellowing) and cellular death. Ultimately, this results in reduced plant vigor, premature leaf drop, reduced aesthetic quality, and declining plant health (CABI 2021; Watson and Kondo 2022). Water-stressed hosts are particularly vulnerable to attack by the Oriental scale (Watson and Kondo 2022), and warmer temperatures further increase population density, posing a threat to palms and ornamentals in Florida urban environments. In addition to damaging the appearance and health of plants in residential and public landscapes, infestations can also affect the role of native or historically important plants in supporting local wildlife and preserving regional plant diversity.
Credit: Adam Dale, UF/IFAS.
Management
As with other armored scale insects, Aonidiella orientalis is most effectively managed with a combination of strategies, including biological, cultural, and chemical controls that will vary depending on the host plant, planting site, and severity of infestation (Watson and Kondo 2022).
Biological Control
Numerous natural enemies (e.g., predators and parasites) can help suppress Aonidiella orientalis populations. Predators include lady beetles (Coleoptera: Coccinellidae) in the genus Chilocorus, such as C. circumdatus (Gyllenhall, 1808), C. baileyii Blackburn, 1890, and C. nigritus (Fabricius, 1798) (Ponsonby 2009; Watson and Kondo 2022). Other predators include the predatory mite, Hemisarcoptes coccophagus Meyer, 1962 (Acari: Hemisarcoptidae) and the green lacewing Chrysoperla carnea (Stephens, 1836) (Neuroptera: Chrysopidae), which are commercially available in Florida and many parts of the world (García Morales et al. 2016; Watson and Kondo 2022). Parasitoid wasps that attack Aonidella orientalis belong to 23 genera across four families within the superfamily Chalcidoidea (Hymenoptera): Aphelinidae, Encyrtidae, Eulophidae, and Azotidae (Watson and Kondo 2022).
Parasitoid wasps are known to be highly effective in keeping Aonidella orientalis populations in check. In Australia, parasitism rates of up to 80% have been reported by Encarsia citrina (Craw, 1891) and Aphytis melinus DeBach, 1959 (Hymenoptera: Aphelinidae) (Elder et al. 1998), both of which are present in Florida, with Aphytis melinus being commercially available. Habitat manipulation to create suitable environments for supporting natural enemy populations is crucial (Gontijo 2019). This includes minimizing impervious surface area around the base of plants, installing trees to promote suitable microclimates and lower high temperatures, and providing habitat that attracts and supports predatory and parasitic insects, which includes plants that provide flower pollen and nectar, structural complexity, and diverse plant species (Raupp et al. 2010; Gontijo 2019; Dale et al. 2020).
Cultural Control
Cultural practices play a vital role in preventing and managing Aonidella orientalis infestations. Key cultural control measures include maintaining plant health through proper irrigation, fertilization, and pruning. Healthy plants are better able to tolerate and recover from infestations. Removal and destruction of heavily infested plant material, such as pruning infested fronds, can significantly reduce scale populations and prevent spread to nearby plants. Additionally, selecting non-host or less susceptible plant species when designing landscapes can reduce long-term pest pressure. Avoiding excessive use of nitrogen fertilizers is also important, as lush new growth may favor scale population growth.
Chemical Control
When necessary, spot treatments of infested plant tissue with mineral oil, such as mineral oil emulsion sprays, can help reduce infestation levels. These oils are considered low impact because they work through physical action rather than chemical toxicity and generally pose less risk to beneficial insects when applied carefully. Insecticide use should be considered only after cultural practices (like pruning heavily infested fronds) and the use of biological control tactics (such as parasitic wasps and predatory beetles) have been considered. Broad-spectrum insecticides, which kill a wide range of insects (including helpful ones) should be avoided whenever possible to prevent unintended toxic effects on natural enemies and other beneficial fauna (Watson and Kondo, 2022). In addition to low-impact products like mineral oils, selective products such as insect growth regulators and products that work through translaminar or systemic activity will likely provide the best control and plant protection. However, systemic insecticides should be avoided on any plants that are attractive to pollinators or that are a food source for other plant-feeding insects. Systemic insecticides can contaminate nectar, pollen, or plant tissue and harm non-target species. Pest management strategies should be implemented with consideration of the ecosystem using an integrated pest management (IPM) approach.
Selected References
Badawi A, Al-Ahmed AM. 1990. The population dynamics of the Oriental scale insect, Aonidiella orientalis (Newstead) and factors affecting its seasonal abundance. Arab Gulf Journal of Scientific Research. 8:81–89.
CABI (Centre for Agriculture and Biosciences International). 2021. Aonidiella orientalis (Oriental yellow scale). Datasheet. Retrieved from www.cabi.org (26 August 2024).
Dale AG, Perry RL, Cope GC, Benda N. 2020. Floral abundance and richness drive beneficial arthropod conservation and biological control on golf courses. Urban Ecosystems. 23:55–66. https://doi.org/10.1007/s11252-019-00907-0
Dekle GW. 1976. Florida armored scale insects. Arthropods of Florida and neighboring land areas. 3:1–345. https://doi.org/10.64338/fsca.af.3.ric9j
Elder RJ, Smith D. 1995. Mass rearing of Aonidiella orientalis (Newstead) (Hemiptera: Diaspididae) on butternut gramma. Journal of the Australian Entomological Society. 34:253–254. https://doi.org/10.1111/j.1440-6055.1995.tb01333.x
European Food Safety Authority Panel on Plant Health. 2022. Pest categorisation of Aonidiella orientalis. EFSA Journal. 20(11): e07642.
Florida Department of Agriculture and Consumer Services, Division of Plant Industry (FDACS-DPI). 2025. Database. Accessed 2 April 2025.
García Morales M, Denno BD, Miller DR, Miller GL, Ben-Dov Y, Hardy NB. 2016. ScaleNet: A literature-based model of scale insect biology and systematics. Database. Retrieved from https://scalenet.info (18 March 2025).
Gontijo LM. 2019. Engineering natural enemy shelters to enhance conservation biological control in field crops. Biological Control. 130:155–163. https://doi.org/10.1016/j.biocontrol.2018.10.014
Mckenzie HL. 1938. The Genus Aonidiella (Homoptera; Coccoidea; Diaspididae). Microentomology. 3(1): 1–36.
Miller DR, Davidson, JA. 2005. Armored Scale Insect Pests of Trees and Shrubs (Hemiptera: Diaspididae). Cornell University Press. Ithaca, USA, 442 pp.
Ponsonby DJ. 2009. Factors affecting utility of Chilocorus nigritus (F.) (Coleoptera: Coccinellidae) as a biocontrol agent. CABI Reviews. 4(46): 1–20. https://doi.org/10.1079/PAVSNNR20094046
Raupp MJ, Shrewsbury PM, Herms DA. 2010. Ecology of herbivorous arthropods in urban landscapes. Annual Review of Entomology. 55:19–38. https://doi.org/10.1146/annurev-ento-112408-085351
Waterhouse DF, Sands DPA. 2001. Classical Biological Control of Arthropods in Australia. CSIRo Entomology. Canberra, Australia, 560 pp.
Watson GW. 2002. Arthropods of economic importance: Diaspididae of the world. Database. Retrieved from https://diaspididae.linnaeus.naturalis.nl (26 August 2024).
Watson GW, Kondo T. 2022. Encyclopedia of Scale Insect Pests. CAB International. Wallingford, UK, 720 pp. https://doi.org/10.1079/9781800620643.0000