Biology, ecology and integrated pest management of the white mango scale, Aulacaspis tubercularis Newstead, a new pest in southern Spain - a review
Introduction
Mango (Mangifera indica L.) ranks as the fifth most consumed fruit in the world, after citrus, banana, grapes and apple with an estimated harvested global area of 5.68 million hectares and a global production of 50.64 million metric tons (FAO, 2019). Mangoes are grown under very diverse climatic conditions in tropical and subtropical regions. Asia is the dominant producing region, with over 74.4%, followed by the Americas and the Caribbean (13.1%), Africa (12.4%), and Oceania (0.1%) (FAO, 2019). Mango is not produced commercially in continental Europe except in Spain, which has approximately 4200 ha of plantations, and a total production of 28000 tons in 2016 (MAPA, 2018), representing only 0.06% of the world's mango production. However, in the last 15 years, there has been a substantial development of this crop in the south of Spain becoming, after avocado, the most important subtropical crop. This increase is mainly due to the privileged climatic conditions for this crop (absence of winter frosts and dry-sunny summers), which allow the production of a high-quality fruit, and the growing demand of this fruit from the main European markets (Hermoso et al., 2018). Most of the Spanish mango production is located on the Andalusian Mediterranean coast (Málaga and Granada provinces) and in the Canary Islands, being exported mainly to other European Union countries such as Portugal (28%), France (27%) and Germany (17%) (Junta de Andalucía, 2017). Until a few years ago, Spanish mango production was characterized by a minimal application of phytosanitary products, which allowed rapid access to the European market with a high-quality product and optimum ripeness.
Mango crops present numerous phytosanitary problems, favored by the special climatic conditions in the producing regions (Peña et al., 1998). Among them, the Mediterranean fruit fly Ceratitis capitata (Wiedemann) (Diptera: Tephritidae) and the white mango scale, Aulacaspis tubercularis Newstead (Hemiptera: Diaspididae) stand out in Spanish mango groves for their constancy and economic importance due to the serious damage they cause to the fruit (Boyero et al., 2017). This has led to an increasing dependence on the use of insecticides, with an increase in associated costs and risks, among them the potential imbalance of secondary pests (Boyero et al., 2017). Scale insects, especially diaspidid scales, are among the most important pests of mangoes in some parts of the world (Waite, 2002). In the case of A. tubercularis, this species is considered one of the key pests of mango crops around the world (Nabil et al., 2012; López-Guillén et al., 2017), because it causes conspicuous pink blemishes on the mango fruits, which depreciate their commercial value and make them unacceptable for export markets (Porcelli, 1990; Nabil et al., 2012). This damage has a significant economic importance, because it can lead to the loss of up to 90% of economic value production if the pest is not controlled in time, mainly in organic crops (Hodges et al., 2005; Urías-López, 2006).
There is currently limited information on A. tubercularis, with most published scientific studies focused on the description of its biological cycle and natural enemies, specifically in South Africa (Daneel and Dreyer, 1997, 1998), Egypt (El-Metwally et al., 2011; Nabil et al., 2012; Abo-Shanab, 2012) and Mexico (Urías-López et al., 2010). In Spain, Arteaga et al. (2003) studied the presence of the pest in the Canary Islands and described the damage. Likewise, Vela et al. (2015) report on the phenology of A. tubercularis and its natural enemies complex in Andalusia. In addition, the efficacy of eco-compatible active substances has been determined (Bienvenido et al., 2017) and the bases for control of A. tubercularis using sexual pheromone have been developed (Ortiz et al., 2017). The present report is an update of the currently available information, aimed to help in the development of integrated management strategies of this pest in the main mango growing areas of Spain and other regions of the Mediterranean Basin.
Section snippets
Origin and geographical distribution in Palearctic region
Aulacaspis tubercularis is considered a cryptogenic and cosmopolitan species endemic to the Asian continent and introduced in other parts of the world together with infested plant material (Takagi, 2010). At present, the pest is widespread in more than 60 mango-growing countries of tropical and subtropical climate regions of the world, including Africa, Asia, Oceania, South and Central America, parts of Europe and the Caribbean (García-Morales et al., 2016; CABI, 2018). It has also been
Taxonomy and nomenclature
Aulacaspis tubercularis belongs to family Diaspididae (Hemiptera: Coccoidea) or armored scale insects, which accounts about 2400 species worldwide, many of them pests of cultivated plants (Miller and Davidson, 2005). This armored scale species was first described by Newstead in 1906 as A. (Diaspis) tubercularis from Java (Newstead, 1908). It was also later described with the names Aulacaspis cinnamomi Newstead and Diaspis (Aulacaspis) cinnamomi var. mangiferae (Newstead, 1911), though Sanders
Life cycle
The biology and ecology of A. tubercularis has been described under field and semi-field conditions in different tropical and subtropical regions, but the limited available data are difficult to compare due to differences in experimental design. However, these studies have shown that the incidence of A. tubercularis is influenced strongly by climatic conditions, with a combination of high mean temperatures and low relative humidity the most appropriate for its development (Urías-López et al.,
Host plants
Newstead (1908) originally described A. tubercularis as a species associated with Cinnamomun zeylanicum (Lauraceae) in Java (Indonesia). Takagi (2010) suggested that A. tubercularis originally developed on indigenous Lauraceae almost exclusively and only subsequently used mango trees and other cultivated species as host plants. Presently, A. tubercularis is considered a highly polyphagous species (Miller and Davidson, 2005) that has been recorded on more than 50 plant species belonging to 30
Damage and economic importance
Aulacaspis tubercularis feeds on mango leaves, branches and fruit, causing severe damage to the plant (Djirata et al., 2017). According to Labuschagne et al. (1995), damage caused by A. tubercularis is primarily aesthetic (chlorosis) and is due to the suction of sap (phloem) by females and immature stages when they feed on leaves, branches and fruits (Juárez-Hernández et al., 2014). Severe attacks can produce a decrease of the photosynthetic capacity, deficient flowering, dryness of young
Cultural control
Some mango cultural control measures have been adopted in the main producing regions to create unfavorable conditions for A. tubercularis. For example, mango tree post-harvest pruning can significantly decrease the number of male colonies and females of A. tubercularis present in the leaves (Bautista-Rosales et al., 2013; Pérez et al., 2016; López-Guillén et al., 2018) and helps the penetration of chemical sprays through the tree canopy (Cunningham, 1991). Mango scales prefer a shaded
Conclusions
The white mango scale, A. tubercularis, is one of the main pests that causes the most economic losses in mango groves in Spain, mainly due to the aesthetic damage it brings on the fruit, which devalues its commercial value (Boyero et al., 2017). Despite being distributed worldwide, the number of studies on its biology, ecology and management are limited. Moreover, in most cases, these studies were carried out more than two decades ago and are generally framed in the growing conditions of other
Declaration of competing interest
The authors declare that they have no known competing financial interests or personal relationships that could have appeared to influence the work reported in this paper.
Acknowledgements
This work was supported by the AVA.AVA2019.038 project of the Junta de Andalucía (Spain), 80% co-financed by European Regional Development Fund (ERDF), within Andalucía ERDF 2014-20 Regional Operational Programme. M. del Pino is currently supported by an INIA-CCAA contract, 20% co-financed by Spanish National Institute for Agricultural and Food Research and Technology (INIA) and 80% by ERDF. Authors are especially grateful to the two anonymous reviewers and the editor for critically reviewing
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