Literature DB >> 35035580

Pest categorisation of Maconellicoccus hirsutus.

Claude Bragard, Paula Baptista, Elisavet Chatzivassiliou, Francesco Di Serio, Paolo Gonthier, Josep Anton Jaques Miret, Annemarie Fejer Justesen, Christer Sven Magnusson, Panagiotis Milonas, Juan A Navas-Cortes, Stephen Parnell, Roel Potting, Philippe Lucien Reignault, Emilio Stefani, Hans-Hermann Thulke, Wopke Van der Werf, Antonio Vicent Civera, Jonathan Yuen, Lucia Zappalà, Jean-Claude Gregoire, Chris Malumphy, Spyridon Antonatos, Virag Kertesz, Andrea Maiorano, Dimitrios Papachristos, Alan MacLeod.   

Abstract

The EFSA Panel on Plant Health performed a pest categorisation of Maconellicoccus hirsutus (Hemiptera: Pseudococcidae), the pink hibiscus mealybug, for the EU. M. hirsutus is native to Southern Asia and has established in many countries in tropical and subtropical regions throughout the world. Within the EU, the pest has been reported from Cyprus and Greece (Rhodes). M. hirsutus is not listed in Annex II of Commission Implementing Regulation (EU) 2019/2072. It is highly polyphagous, feeding on plants assigned to 229 genera in 78 plant families, and shows some preference for hosts in the families Malvaceae, Fabaceae and Moraceae. Economically important crops in the EU such as cotton (Gossypium spp.), citrus (Citrus spp.), ornamentals (Hibiscus spp.), grapes (Vitis vinifera), soybean (Glycinae max), avocado (Persea americana) and mulberry trees (Morus alba) may be significantly affected by M. hirsutus. The lower and upper developmental temperature threshold of M. hirsutus on Hibiscus rosa-sinensis are 14.5 and 35.0°C, respectively, with optimal female development estimated to be at 29.0°C. There are about 10 generations a year in the subtropics but as many as 15 may occur under optimal conditions. Plants for planting, fruits, vegetables and cut flowers provide potential pathways for entry into the EU. Climatic conditions in EU member states around the Mediterranean Sea and host plant availability in those areas are conducive for establishment. The introduction of M. hirsutus is expected to have an economic impact in the EU through damage to various ornamental plants, as already observed in Cyprus and Greece, and reduction in yield and quality of many significant crops. Phytosanitary measures are available to reduce the likelihood of entry and further spread. Some uncertainties include the area of establishment, whether it could become a greenhouse pest, impact, and the influence of natural enemies. M. hirsutus meets the criteria that are within the remit of EFSA to assess for it to be regarded as a potential Union quarantine pest.
© 2022 European Food Safety Authority. EFSA Journal published by John Wiley and Sons Ltd on behalf of European Food Safety Authority.

Entities:  

Keywords:  Hemiptera; Pseudococcidae; pest risk; pink hibiscus mealybug; plant health; plant pest; quarantine

Year:  2022        PMID: 35035580      PMCID: PMC8749475          DOI: 10.2903/j.efsa.2022.7024

Source DB:  PubMed          Journal:  EFSA J        ISSN: 1831-4732


Introduction

Background and Terms of Reference as provided by the requestor

Background

The new Plant Health Regulation (EU) 2016/2031, on the protective measures against pests of plants, is applying from 14 December 2019. Conditions are laid down in this legislation in order for pests to qualify for listing as Union quarantine pests, protected zone quarantine pests or Union regulated non‐quarantine pests. The lists of the EU regulated pests together with the associated import or internal movement requirements of commodities are included in Commission Implementing Regulation (EU) 2019/2072. Additionally, as stipulated in the Commission Implementing Regulation 2018/2019, certain commodities are provisionally prohibited to enter in the EU (high risk plants, HRP). EFSA is performing the risk assessment of the dossiers submitted by exporting to the EU countries of the HRP commodities, as stipulated in Commission Implementing Regulation 2018/2018. Furthermore, EFSA has evaluated a number of requests from exporting to the EU countries for derogations from specific EU import requirements. In line with the principles of the new plant health law, the European Commission with the Member States are discussing monthly the reports of the interceptions and the outbreaks of pests notified by the Member States. Notifications of an imminent danger from pests that may fulfil the conditions for inclusion in the list of the Union quarantine pest are included. Furthermore, EFSA has been performing horizon scanning of media and literature. As a follow‐up of the above‐mentioned activities (reporting of interceptions and outbreaks, HRP, derogation requests and horizon scanning), a number of pests of concern have been identified. EFSA is requested to provide scientific opinions for these pests, in view of their potential inclusion by the risk manager in the lists of Commission Implementing Regulation (EU) 2019/2072 and the inclusion of specific import requirements for relevant host commodities, when deemed necessary by the risk manager.

Terms of reference

EFSA is requested, pursuant to Article 29(1) of Regulation (EC) No 178/2002, to provide scientific opinions in the field of plant health. EFSA is requested to deliver 53 pest categorisations for the pests listed in Annex 1A, 1B, 1D and 1E (for more details see mandate M‐2021‐00027 on the Open.EFSA portal). Additionally, EFSA is requested to perform pest categorisations for the pests so far not regulated in the EU, identified as pests potentially associated with a commodity in the commodity risk assessments of the HRP dossiers (Annex 1C; for more details see mandate M‐2021‐00027 on the Open.EFSA portal). Such pest categorisations are needed in the case where there are not available risk assessments for the EU. When the pests of Annex 1A are qualifying as potential Union quarantine pests, EFSA should proceed to phase 2 risk assessment. The opinions should address entry pathways, spread, establishment, impact and include a risk reduction options analysis. Additionally, EFSA is requested to develop further the quantitative methodology currently followed for risk assessment, in order to have the possibility to deliver an express risk assessment methodology. Such methodological development should take into account the EFSA Plant Health Panel Guidance on quantitative pest risk assessment and the experience obtained during its implementation for the Union candidate priority pests and for the likelihood of pest freedom at entry for the commodity risk assessment of High Risk Plants.

Interpretation of the Terms of Reference

Maconellicoccus hirsutus is one of a number of pests listed in Annex 1A to the Terms of Reference (ToR) (Section 1.1.2) to be subject to pest categorisation to determine whether it fulfils the criteria of a potential Union quarantine pest for the area of the EU excluding Ceuta, Melilla and the outermost regions of Member States referred to in Article 355(1) of the Treaty on the Functioning of the European Union (TFEU), other than Madeira and the Azores, and so inform European Commission decision making as to its appropriateness for potential inclusion in the lists of pests of Commission Implementing Regulation (EU) 2019/2072. If a pest fulfils the criteria to be potentially listed as a Union quarantine pest, risk reduction options will be identified.

Additional information

This pest categorisation was initiated following the commodity risk assessment of Ficus carica plants from Israel performed by EFSA (EFSA PLH Panel, 2021), in which M. hirsutus was identified as a relevant non‐regulated EU pest which could potentially enter the EU on F. carica.

Data and methodologies

Data

Information on pest status from NPPOs

In the context of the commodity risk assessment of Ficus carica plants from Israel (EFSA PLH Panel, 2021), EFSA consulted (in April‐May 2020) the NPPOs where the pest is present, in order to have an updated information on the pest status. For the information on pest status in Cyprus and Greece, please see Section 3.2.2.

Literature search

A literature search on M. hirsutus was conducted at the beginning of the categorisation in the ISI Web of Science bibliographic database, using the scientific name of the pest as search term. Papers relevant for the pest categorisation were reviewed, and further references and information were obtained from experts, as well as from citations within the references and grey literature.

Database search

Pest information, on host(s) and distribution, was retrieved from the European and Mediterranean Plant Protection Organization (EPPO) Global Database (EPPO, online), the CABI databases and scientific literature databases as referred above in Section 2.1.2. Data about the import of commodity types that could potentially provide a pathway for the pest to enter the EU and about the area of hosts grown in the EU were obtained from EUROSTAT (Statistical Office of the European Communities). The Europhyt and TRACES databases were consulted for pest‐specific notifications on interceptions and outbreaks. Europhyt is a web‐based network run by the Directorate General for Health and Food Safety (DG SANTÉ) of the European Commission as a subproject of PHYSAN (Phyto‐Sanitary Controls) specifically concerned with plant health information. TRACES is the European Commission's multilingual online platform for sanitary and phytosanitary certification required for the importation of animals, animal products, food and feed of non‐animal origin and plants into the EU, and the intra‐EU trade and EU exports of animals and certain animal products. Up until May 2020, the Europhyt database managed notifications of interceptions of plants or plant products that do not comply with EU legislation, as well as notifications of plant pests detected in the territory of the Member States and the phytosanitary measures taken to eradicate or avoid their spread. The recording of interceptions switched from Europhyt to TRACES in May 2020.

Methodologies

The Panel performed the pest categorisation for M. hirsutus, following guiding principles and steps presented in the EFSA guidance on quantitative pest risk assessment (EFSA PLH Panel, 2018), the EFSA guidance on the use of the weight of evidence approach in scientific assessments (EFSA Scientific Committee, 2017) and the International Standards for Phytosanitary Measures No. 11 (FAO, 2013). The criteria to be considered when categorising a pest as a potential Union quarantine pest (QP) is given in Regulation (EU) 2016/2031 Article 3 and Annex I, Section 1 to this Regulation. Table 1 presents the Regulation (EU) 2016/2031 pest categorisation criteria on which the Panel bases its conclusions. In judging whether a criterion is met the Panel uses its best professional judgement (EFSA Scientific Committee, 2017) by integrating a range of evidence from a variety of sources (as presented above in Section 2.1) to reach an informed conclusion as to whether or not a criterion is satisfied.
Table 1

Pest categorisation criteria under evaluation, as defined in Regulation (EU) 2016/2031 on protective measures against pests of plants (the number of the relevant sections of the pest categorisation is shown in brackets in the first column)

Criterion of pest categorisation Criterion in Regulation (EU) 2016/2031 regarding Union quarantine pest (article 3)
Identity of the pest (Section  3.1 ) Is the identity of the pest established, or has it been shown to produce consistent symptoms and to be transmissible?
Absence/presence of the pest in the EU territory (Section  3.2 )

Is the pest present in the EU territory?

If present, is the pest widely distributed within the EU? Describe the pest distribution briefly

Regulatory status (Section  3.3 ) If the pest is present in the EU but not widely distributed in the risk assessment area, it should be under official control or expected to be under official control in the near future
Pest potential for entry, establishment and spread in the EU territory (Section  3.4 ) Is the pest able to enter into, become established in, and spread within, the EU territory? If yes, briefly list the pathways
Potential for consequences in the EU territory (Section  3.5 ) Would the pests’ introduction have an economic or environmental impact on the EU territory?

Available measures

(Section  3.6 )

Are there measures available to prevent the entry into the EU such that the likelihood of introduction becomes mitigated?
Conclusion of pest categorisation (Section  4 ) A statement as to whether (1) all criteria assessed by EFSA above for consideration as a potential quarantine pest were met and (2) if not, which one(s) were not met
Pest categorisation criteria under evaluation, as defined in Regulation (EU) 2016/2031 on protective measures against pests of plants (the number of the relevant sections of the pest categorisation is shown in brackets in the first column) Is the pest present in the EU territory? If present, is the pest widely distributed within the EU? Describe the pest distribution briefly Available measures (Section  3.6 ) The Panel’s conclusions are formulated respecting its remit and particularly with regard to the principle of separation between risk assessment and risk management (EFSA founding regulation (EU) No 178/2002); therefore, instead of determining whether the pest is likely to have an unacceptable impact, deemed to be a risk management decision, the Panel will present a summary of the observed impacts in the areas where the pest occurs, and make a judgement about potential likely impacts in the EU. While the Panel may quote impacts reported from areas where the pest occurs in monetary terms, the Panel will seek to express potential EU impacts in terms of yield and quality losses and not in monetary terms, in agreement with the EFSA guidance on quantitative pest risk assessment (EFSA PLH Panel, 2018). Article 3 (d) of Regulation (EU) 2016/2031 refers to unacceptable social impact as a criterion for quarantine pest status. Assessing social impact is outside the remit of the Panel.

Pest categorisation

Identity and biology of the pest

Identity and taxonomy

Is the identity of the pest established, or has it been shown to produce consistent symptoms and/or to be transmissible? Yes, the identity of the pest is established and Maconellicoccus hirsutus (Green) is the accepted name. The pink hibiscus mealybug, also known as the hibiscus mealybug, Maconellicoccus hirsutus (Green, 1908) is an insect within the order Hemiptera, family Pseudococcidae. This species was initially described by Green in 1908 as Phenacoccus hirsutus from specimens collected on an undetermined shrub attended by ants in India (García Morales et al., 2016). Indeed, this species is likely to be native to southern Asia (Williams, 2004). Former scientific names include Maconellicoccus pasaniae, Maconellicoccus perforatus, Paracoccus pasaniae, Phenacoccus glomeratus, Phenacoccus hirsutus, Phenacoccus quaternus, Pseudococcus hibisci and Spilococcus perforatus (CABI, 2021). The genus Maconellicoccus includes eight described species (Williams, 1996; CABI, 2021). Detailed morphological descriptions, illustrations and keys to the eight species of the genus Maconellicoccus can be found in Williams (1996), Meyerdirk et al. (2001) and EPPO (2006). The EPPO code (Griessinger & Roy, 2015; EPPO, 2019) for this species is PHENHI (EPPO, 2021).

Biology of the pest

Adult females of M. hirsutus in Jordan appear in early February and show their highest abundance in mid‐July (Al‐Fwaeer et al., 2014). M. hirsutus reproduces parthenogenetically or sexually (Williams, 1996). Reproduction is mostly parthenogenetic in Egypt and the State of Bihar, India (Hall, 1921; Singh and Ghosh, 1970), while it is sexual in the Indian state of West Bengal (Ghose, 1971) and probably in the Caribbean (Williams, 1996). According to Bartlett (1978) and Mani (1989), an adult female lays 150–600 eggs over a period of about 1 week on the host plants. The eggs are laid in an ovisac, consisting of a mass of sticky wax filaments. Oviposition occurs mainly in the outer parts of the host, such as the growing points, buds and fruits, but in case of cold weather conditions the females search for shelter to oviposit (Meyerdirk et al., 2001). The lower and upper developmental temperature threshold of M. hirsutus on Hibiscus rosa‐sinensis are 14.5 and 35.0°C, respectively. The optimal developmental temperature for females was estimated to be 29.0°C (Chong et al., 2008). In warm, but unspecified conditions, it takes 5 weeks for a generation to be completed (Bartlett, 1978). Chong et al. (2008) stated that the generation time is 41 days at 25°C and 82 days at 20°C. In countries with a cool winter the species overwinters as eggs (Bartlett, 1978) or other stages in protected parts of the host plant or as eggs in the soil (Pollard, 1995). There are about 10 generations a year in the subtropics (Meyerdirk et al., 2001). However, under optimum conditions, there may be as many as 15 generations per year (Pollard, 1995). There are three immature instars in the female and four in the male (EPPO, 2005). First instar nymphs are known as crawlers and are mobile. The crawlers prefer the apical and tender regions of the host. However, large populations of nymphs may also settle on the older plant parts including stems, leaves, petioles, roots, tubers and pods (Ghose, 1972). After locating a suitable feeding site on a host plant, nymphs settle to feed and develop. Later instars turn grey–pink and start to secrete white wax that covers their bodies (Chong et al., 2015). In heavy infestations white masses of wax concealing the insect may occur in axils and on twigs and stems (EPPO, 2006) (Figure 1). Female adults live for 19–28 days (Chong et al., 2008; Sahito et al., 2012; Negrini et al., 2017). Males have one pair of wings, but they are weak flyers, only live a day or two, and are not commonly observed (Chong et al., 2015).
Figure 1

Maconellicoccus hirsutus: (A) adult female; (B) adult female covered in waxy filaments; (C) large infestation on hibiscus; (D) ovisacs in the crevices of Annona fruit; (E) distorted growth characteristic of plants infested by M. hirsutus; (F) hibiscus plant in Rhodes, severely damaged by M. hirsutus © Chris Malumphy

Maconellicoccus hirsutus: (A) adult female; (B) adult female covered in waxy filaments; (C) large infestation on hibiscus; (D) ovisacs in the crevices of Annona fruit; (E) distorted growth characteristic of plants infested by M. hirsutus; (F) hibiscus plant in Rhodes, severely damaged by M. hirsutus © Chris Malumphy Key features of the biology of each life stage are summarised in Table 2.
Table 2

Important features of the life history strategy of Maconellicoccus hirsutus

Life stagePhenology and relation to hostOther relevant information
Egg Adult female lays 150–600 eggs in a sticky waxy ovisac. Oviposition occurs mainly on the outer areas of the host, including the buds and fruitThe eggs hatch in 6–9 days at temperatures between 25 and 35°C but it requires 16 days at 20°C. The lower and upper threshold for the eggs and the optimal developmental temperature were estimated at 14.5, 39.8 and 33.4°C, respectively (Chong et al., 2008)
First instar nymph First instar nymphs are known as crawlers. They prefer the apical and tender parts of the host. However, large populations of nymphs may also settle on the older plant parts including stems, leaves, petioles, roots, tubers, and pods. After locating a suitable host plant, nymphs settle on the host to feed and developThe crawlers disperse by walking to other parts of the host plant. They may also be transported by water, wind or animals
Later instar nymphs Later instars start to secrete white wax that covers their bodies. There are three immature instars in the female and four in the maleWhite masses of wax concealing the insect may occur in axils and on twigs and stems. The nymphal development is affected by both temperature and host plant. At 25°C, the female nymphs need 23 and 26.6 days on H. rosa‐sinensis and Morus alba, respectively, to complete their development (Chong et al., 2008; Sahito et al., 2012). On H. rosa‐sinensis and at 27°C nymphal development was reported to last either 17.5 or 20.6 days (Chong et al., 2008; Negrini et al., 2017). Whereas at 30 and 20°C the female nymphal stages last 26.6 and 50.1 days, respectively. The lower and upper threshold and the optimal developmental temperature for female nymphs were estimated at 15.1, 35.0 and 28.8°C, respectively (Chong et al., 2008)
Adult Males have one pair of wings, but they are weak flyers. Female adults live for 19–28 days (Chong et al., 2008; Sahito et al., 2012; Negrini et al., 2017) while males only 1 or 2 days and are not commonly observed (Chong et al., 2015) M. hirsutus reproduces parthenogenetically or sexually. The lower and upper developmental temperature threshold on H. rosa‐sinensis were 14.5 and 35°C, respectively. The optimal developmental temperature for females was estimated to be 29°C
Important features of the life history strategy of Maconellicoccus hirsutus

Host range/species affected

There is a long list of host plants of M. hirsutus worldwide. The host range of M. hirsutus is broad with more than 229 plant genera from 78 plant families (García Morales et al., 2016). Appendix A provides the full list of plant species reported to be M. hirsutus hosts. Economically important crops in the EU such as cotton (Gossypium spp.), citrus (Citrus spp.), ornamentals (Hibiscus spp.), grapes (Vitis vinifera), soybean (Glycinae max), avocado (Persea americana) and mulberry trees (Morus alba) may be significantly affected by M. hirsutus. M. hirsutus has also been recorded on several rosaceous crops that are important in the EU, including apple (Malus domestica), apricot (Prunus armeniaca), peach (Prunus persica), pear (Pyrus communis) and plum (Prunus domestica), but there appears to be no economic impact recorded on these hosts.

Intraspecific diversity

No intraspecific diversity is reported for this species.

Detection and identification of the pest

Are detection and identification methods available for the pest? Yes. There are methods available for detection, and morphological and molecular identification of M. hirsutus.

Detection

Careful visual examination of plants is an effective way for the detection of the insect. The white waxy covering of mealybug instars and white waxy filaments in the egg mass allow detection (Meyerdirk et al., 2001). The mealybugs themselves are in general visible, although they are hidden in the swollen growth. Male adults can also be caught using sticky cards baited with a sex pheromone which contains esters of lavandulyl and maconellyl and allow detection in areas of low density of the pest (Francis et al., 2007).

Symptoms

The main symptoms of M. hirsutus infestation are (Dufour and Léon, 1997; Sagarra and Peterkin, 1999; Kairo et al., 2000; Alleyne, 2004; Chong et al., 2015): large quantities of honeydew black sooty mould leaf curling shoot and leave malformation fruit malformation bunchy top appearance premature senescence of flowers and foliage heavy infestation may cause a complete defoliation of the plant, leading to their death

Identification

The identification of M. hirsutus requires microscopic examination of slide‐mounted adult females and verification of the presence of key morphological characteristics as given in Meyerdirk et al. (2001) and Williams (1996). Moreover, a key is available (EPPO, 2006) to distinguish M. hirsutus from other species of the genus. Molecular techniques for species identification have also been developed (Malausa et al., 2011; Abd‐Rabou et al., 2012). Description (detailed morphological descriptions are available from Meyerdirk et al. (2001) and EPPO (2006)) The main morphological characteristics of M. hirsutus are: The eggs are 0.3 mm long and initially orange, turning pink before hatching (Chong et al., 2015). Crawlers 0.37 mm long (Aristizábal et al., 2012), pink and oval with antennae; they lack the waxy body coating (CABI, 2021). Second instars average length 0.70 mm, third instars 1.1 mm and male fourth instar 1.1 mm (Aristizábal et al., 2012). Immature females and newly matured females have greyish‐pink bodies dusted with mealy white wax (CABI, 2021). Mature adult females are wingless, elongate oval, slightly flattened in profile, 2.5–4 mm long, and their ovisacs cover most of the body. Body is greyish pink or occasionally purple, and covered with a thin white cotton like wax forming a protective ovisac for her eggs. The entire colony tends to become covered by white, waxy ovisac material (EPPO, 2005, 2006; Chong et al., 2015). On microscopic examination of slide‐mounted females, the combination of nine‐segmented antennae, anal lobe bars, numerous large dorsal oral rim ducts on all parts of the body, and long, flagellate dorsal setae make the species fairly easy to recognize in parts of the world where other Maconellicoccus species do not occur. Males have one pair of very simple wings, long antennae, white wax filaments projecting posteriorly and lack mouthparts CABI (2021).

Pest distribution

Pest distribution outside the EU

M. hirsutus has established in many tropical and subtropical regions throughout the world in the past 100 years (Culik et al., 2013). It has a wide distribution which includes many countries in Africa, South Asia, Australia, Central America, South America, Caribbean and the southern part of North America (EPPO, 2021) (Figure 2). For a detailed list of countries where M. hirsutus is present, see Appendix B.
Figure 2

Global distribution of Maconellicoccus hirsutus (Source: EPPO Global Database accessed on 15/10/2021)

Global distribution of Maconellicoccus hirsutus (Source: EPPO Global Database accessed on 15/10/2021)

Pest distribution in the EU

Is the pest present in the EU territory? If present, is the pest widely distributed within the EU? M. hirsutus has a restricted distribution in the EU. It is present in Greece and Cyprus. The pest is widespread only in the island of Rhodes in southern eastern part of Greece. The pest is present, widespread and under official control in Cyprus (EPPO GD, online). According to Miller et al. (2014), between 1995 and 2012 the species had been intercepted in USA ports in commodities originating from France and Italy. However, there are no records of the species from France and Italy. This has probably resulted from produce being imported to Europe from areas where the mealybug occurs and re‐exported to the USA.

Regulatory status

Commission Implementing Regulation 2019/2072

M. hirsutus is not listed in Annex II of Commission Implementing Regulation (EU) 2019/2072.

Hosts or species affected that are prohibited from entering the Union from third countries

According to the Commission Implementing Regulation (EU) 2019/2072, Annex VI, introduction of several M. hirsutus hosts in the Union from certain third countries is prohibited (Table 3).
Table 3

List of plants, plant products and other objects that are Maconellicoccus hirsutus hosts whose introduction into the Union from certain third countries is prohibited (Source Commission Implementing Regulation (EU) 2019/2072, Annex VI)

List of plants, plant products and other objects whose introduction into the Union from certain third countries is prohibited
DescriptionCN CodeThird country, group of third countries or specific area of third country
8.Plants for planting of Chaenomeles Ldl., Crateagus L., Cydonia Mill., Malus Mill., Prunus L., Pyrus L. and Rosa L., other than dormant plants free from leaves, flowers and fruits

ex 0602 10 90

ex 0602 20 20

ex 0602 20 80

ex 0602 40 00

ex 0602 90 41

ex 0602 90 45

ex 0602 90 46

ex 0602 90 47

ex 0602 90 48

ex 0602 90 50

ex 0602 90 70

ex 0602 90 91

ex 0602 90 99

Third countries other than: Albania, Andorra, Armenia, Azerbaijan, Belarus, Bosnia and Herzegovina, Canary Islands, Faeroe Islands, Georgia, Iceland, Liechtenstein, Moldova, Monaco, Montenegro, North Macedonia, Norway, Russia (only the following parts: Central Federal District (Tsentralny federalny okrug), Northwestern Federal District (Severo‐Zapadny federalny okrug), Southern Federal District (Yuzhny federalny okrug), North Caucasian Federal District (Severo‐Kavkazsky federalny okrug) and Volga Federal District (Privolzhsky federalny okrug)), San Marino, Serbia, Switzerland, Turkey and Ukraine
9.Plants for planting of Cydonia Mill., Malus Mill., Prunus L. and Pyrus L. and their hybrids, and Fragaria L., other than seeds

ex 0602 10 90

ex 0602 20 20

ex 0602 90 30

ex 0602 90 41

ex 0602 90 45

ex 0602 90 46

ex 0602 90 48

ex 0602 90 50

ex 0602 90 70

ex 0602 90 91

ex 0602 90 99

Third countries, other than: Albania, Algeria, Andorra, Armenia, Australia, Azerbaijan, Belarus, Bosnia and Herzegovina, Canada, Canary Islands, Egypt, Faeroe Islands, Georgia, Iceland, Israel, Jordan, Lebanon, Libya, Liechtenstein, Moldova, Monaco, Montenegro, Morocco, New Zealand, North Macedonia, Norway, Russia (only the following parts: Central Federal District (Tsentralny federalny okrug), Northwestern Federal District (Severo‐Zapadny federalny okrug), Southern Federal District (Yuzhny federalny okrug), North Caucasian Federal District (Severo‐Kavkazsky federalny okrug) and Volga Federal District (Privolzhsky federalny okrug)), San Marino, Serbia, Switzerland, Syria, Tunisia, Turkey, Ukraine, and United States other than Hawaii
10.Plants of Vitis L., other than fruits

0602 10 10

0602 20 10

ex 0604 20 90

ex 1404 90 00

Third countries other than Switzerland
11.Plants of Citrus L., Fortunella Swingle, Poncirus Raf., and their hybrids, other than fruits and seed

ex 0602 10 90

ex 0602 20 20

0602 20 30

ex 0602 20 80

ex 0602 90 45

ex 0602 90 46

ex 0602 90 47

ex 0602 90 50

ex 0602 90 70

ex 0602 90 91

ex 0602 90 99

ex 0604 20 90

ex 1404 90 00

18.

Plants for planting of Solanaceae

other than seeds and the plants

covered by entries 15, 16 or 17

ex 0602 90 30

ex 0602 90 45

ex 0602 90 46

ex 0602 90 48

ex 0602 90 50

ex 0602 90 70

ex 0602 90 91

ex 0602 90 99

Third countries other than: Albania, Algeria, Andorra, Armenia, Azerbaijan, Belarus, Bosnia and Herzegovina, Canary Islands, Egypt, Faeroe Islands, Georgia, Iceland, Israel, Jordan, Lebanon, Libya, Liechtenstein, Moldova, Monaco, Montenegro, Morocco, North Macedonia, Norway, Russia (only the following parts: Central Federal District (Tsentralny federalny okrug), Northwestern Federal District (Severo‐Zapadny federalny okrug), Southern Federal District (Yuzhny federalny okrug), North Caucasian Federal District (Severo‐Kavkazsky federalny okrug) and Volga Federal District (Privolzhsky federalny okrug)), San Marino, Serbia, Switzerland, Syria, Tunisia, Turkey and Ukraine
20.Growing medium as such, other than soil, consisting in whole or in part of solid organic substances, other than that composed entirely of peat or fibre of Cocos nucifera L., previously not used for growing of plants or for any agricultural purposes

ex 2530 10 00

ex 2530 90 00

ex 2703 00 00

ex 3101 00 00

ex 3824 99 93

Third countries other than Switzerland
List of plants, plant products and other objects that are Maconellicoccus hirsutus hosts whose introduction into the Union from certain third countries is prohibited (Source Commission Implementing Regulation (EU) 2019/2072, Annex VI) ex 0602 10 90 ex 0602 20 20 ex 0602 20 80 ex 0602 40 00 ex 0602 90 41 ex 0602 90 45 ex 0602 90 46 ex 0602 90 47 ex 0602 90 48 ex 0602 90 50 ex 0602 90 70 ex 0602 90 91 ex 0602 90 99 ex 0602 10 90 ex 0602 20 20 ex 0602 90 30 ex 0602 90 41 ex 0602 90 45 ex 0602 90 46 ex 0602 90 48 ex 0602 90 50 ex 0602 90 70 ex 0602 90 91 ex 0602 90 99 0602 10 10 0602 20 10 ex 0604 20 90 ex 1404 90 00 ex 0602 10 90 ex 0602 20 20 0602 20 30 ex 0602 20 80 ex 0602 90 45 ex 0602 90 46 ex 0602 90 47 ex 0602 90 50 ex 0602 90 70 ex 0602 90 91 ex 0602 90 99 ex 0604 20 90 ex 1404 90 00 Plants for planting of Solanaceae other than seeds and the plants covered by entries 15, 16 or 17 ex 0602 90 30 ex 0602 90 45 ex 0602 90 46 ex 0602 90 48 ex 0602 90 50 ex 0602 90 70 ex 0602 90 91 ex 0602 90 99 ex 2530 10 00 ex 2530 90 00 ex 2703 00 00 ex 3101 00 00 ex 3824 99 93

Entry, establishment and spread in the EU

Entry

Is the pest able to enter into the EU territory? If yes, identify and list the pathways. Comment on plants for planting as a pathway. Yes. The pest has already entered the EU territory. The main pathways are plants for planting, fruits, vegetables and cut flowers. Plants for planting, fruits, vegetables and cut flowers are the main pathways for entry of M. hirsutus (EPPO, 2005; Culik et al., 2013). It can also be associated with soil, which could however be considered as a closed pathway (Table 4).
Table 4

Potential pathways for Maconellicoccus hirsutus into the EU 27

Pathways description

(e.g. host/intended use/source)

Life stageRelevant mitigations [e.g. prohibitions (Annex VI), special requirements (Annex VII) or phytosanitary certificates (Annex XI) within Implementing Regulation 2019/2072]
Plants for plantingEggs, nymphs and adults

Plants for planting that are hosts of M. hirsutus, and are prohibited to import from third countries (Regulation 2019/2072, Annex VI), are listed in Table 3.

The growing medium attached to or associated with plants, intended to sustain the vitality of the plants, are regulated in Regulation 2019/2072, Annex VII.

Plants for planting from third countries require a phytosanitary certificate (Regulation 2019/2072, Annex XI, Part A)

Fruits, vegetables and cut flowersEggs, nymphs and adults

Fruits, vegetables and cut flowers from third countries require a phytosanitary certificate to import into the EU (2019/2072, Annex XI, Part A). However, no requirements are specified for M. hirsutus.

According to Regulation 2019/2072, Annex XI, Part C there is a list of plants which a phytosanitary certificate is not required for their introduction into the Union territory. M. hirsutus infests fruits that are included in that list (Ananas comosus and Musa spp.)

SoilEggsImport of soil from third countries is prohibited (Regulation 2019/2072, Annex VI)
Potential pathways for Maconellicoccus hirsutus into the EU 27 Pathways description (e.g. host/intended use/source) Plants for planting that are hosts of M. hirsutus, and are prohibited to import from third countries (Regulation 2019/2072, Annex VI), are listed in Table 3. The growing medium attached to or associated with plants, intended to sustain the vitality of the plants, are regulated in Regulation 2019/2072, Annex VII. Plants for planting from third countries require a phytosanitary certificate (Regulation 2019/2072, Annex XI, Part A) Fruits, vegetables and cut flowers from third countries require a phytosanitary certificate to import into the EU (2019/2072, Annex XI, Part A). However, no requirements are specified for M. hirsutus. According to Regulation 2019/2072, Annex XI, Part C there is a list of plants which a phytosanitary certificate is not required for their introduction into the Union territory. M. hirsutus infests fruits that are included in that list (Ananas comosus and Musa spp.) The import of some host plants of M. hirsutus for planting from third countries is not allowed (Regulation 2019/2072, Annex VI), while there are many other hosts that can be imported to the EU with a phytosanitary certificate. Vegetables, cut flowers and most fruits that are imported into the EU must have a phytosanitary certificate. However, pineapple (Ananas comosus) and banana (Musa spp.), which are hosts for M. hirsutus, are exempt by Regulation 2019/2072, Annex XI, Part C. EU legislation (2019/2072) prohibits the import of soil from third countries so that pathway can be considered as closed. Annual imports of M. hirsutus hosts from countries where the pest is known to occur are provided in Appendix C. Notifications of interceptions of harmful organisms began to be compiled in Europhyt in May 1994 and in TRACES in May 2020. As at 16/9/2021 (search date) there were two records of interceptions of M. hirsutus in the Europhyt and TRACES databases: in 2008 on Colocasia sp. plants for planting imported from India in 2018 on Annona squamosa fruits imported from Brazil In the UK, a former member of the EU, there were more than 240 interceptions of M. hirsutus between 1994 and 2021, mostly on Annona squamosa fruits from India. M. hirsutus was also found on Annona fruits from Egypt, Indonesia, Kenya, Pakistan, Saint Lucia and Vietnam, and a range of fresh fruits and vegetables imported from Asia, Africa, and the Caribbean (Fera unpublished records). No action was taken against these findings.

Establishment

Is the pest able to become established in the EU territory? Yes, in the EU countries of southern Europe the climate is suitable and there are many available hosts that can support establishment. Given that M. hirsutus occurs in Greece and has a wide distribution in Cyprus, it must have been able to transfer following entry.

EU distribution of main host plants

M. hirsutus is a polyphagous pest. The main hosts of the pest cultivated in the EU 27 between 2016 and 2020 are shown in Table 5. Among others, citrus, cotton, soybeans, grapes, pome fruits and stone fruits are highly economically important crops in the EU.
Table 5

Crop area of Maconellicoccus hirsutus hosts in EU 27 in 1,000 ha (Eurostat accessed on 21/09/2021)

Crop20162017201820192020
Citrus519.01502.84508.99512.53487.08
Cotton301.34326.12345.64361.78349.94
Soybeans831.18962.39955.40907.91939.86
Grapes3,136.043,133.213,135.023,158,323,160.27
Cucumbers32.3331.8132.6533.6933.15
Bananas20.3018.9117.9418.1919.61
Pome fruitsNo data627.98629.42610.11589.85
Stone fruitsNo data625.46621.32612.33No data
Avocados12.2412.7213.2215.5217.27
Crop area of Maconellicoccus hirsutus hosts in EU 27 in 1,000 ha (Eurostat accessed on 21/09/2021)

Climatic conditions affecting establishment

M. hirsutus occurs mainly in tropical and subtropical regions in Asia, Africa, Australia, and America. Moreover, it has also been recorded in Greece, Cyprus and Turkey, countries with a Mediterranean climate. According to the global Köppen‐Geiger climate zones (Kottek et al., 2006), M. hirsutus is present in countries with climate zones Aw (Equatorial savannah with dry winter), Am (Equatorial monsoon), Af (Equatorial rainforest, fully humid), BWh (Desert climate, hot desert), Bsh (Steppe climate, hot steppe) and Csa (warm temperate climate with dry hot summer). The lower and upper developmental temperature threshold of M. hirsutus on H. rosa‐sinensis is 14.5 and 35°C, respectively (Chong et al., 2008), temperatures that are relatively high. Figure 3 shows the World distribution of Köppen–Geiger climate types that occur in the EU and which occur in countries where M. hirsutus has been reported. Southern EU countries provide suitable climatic conditions that would support the establishment of M. hirsutus. There is uncertainty as to whether M. hirsutus could establish in the EU countries of central Europe. It is unlikely that the insect could establish in the northern EU, and if it did, the populations are likely to be small and have no impact. Countries and areas of the EU most suitable include Cyprus, Greece, Malta, Portugal, Spain, coastal areas of southern France, including Corsica, as well as southern Italy, including Sardinia and Sicily. There is a possibility that M. hirsutus could occur in glasshouses and on indoor plantings in cooler areas.
Figure 3

World distribution of Köppen–Geiger climate types that occur in the EU and which occur in areas where Maconellicoccus hirsutus has been reported

World distribution of Köppen–Geiger climate types that occur in the EU and which occur in areas where Maconellicoccus hirsutus has been reported

Spread

Describe how the pest would be able to spread within the EU territory following establishment? First instar nymphs are spread by crawling, wind, rainfall and on humans and animals. Overwintering eggs may be moved in soil. All stages may be moved over long distances in trade. Comment on plants for planting as a mechanism of spread. Plants for planting are one of the main pathways of spread of the pest over long distances. First instar nymphs are active and spread by crawling, wind and rainfall. The sticky egg masses and mobile crawlers may also be carried to new areas on humans and other animals (Sagarra and Peterkin, 1999; EPPO, 2005; Culik et al., 2013). Moreover, overwintering eggs can be found in soil (Pollard, 1995) and spread through the soil attached to plants for planting and machinery. The introduction of this pest to new territories over long distance is possible through the movement of infested plants for planting (e.g. fruit tree and ornamental nursery seedlings), and trade of infested fruit, vegetables, cut flowers or other plant products (Meyerdirk et al., 2001; CABI, 2021). Plants for planting, fruits, vegetables and cut flowers are the main pathways of spread of the pest over long distances.

Impacts

Would the pests’ introduction have an economic or environmental impact on the EU territory? Yes, if M. hirsutus established more widely in the EU, it would most probably have an economic impact on the host species of the pest. The pest may seriously affect the commercial value of various ornamental plants and potentially have a high economic impact on crop production in the EU. M. hirsutus egests large quantities of honeydew, and as a result black sooty mould develops on the plants, which reduces the aesthetic value, normal growth and reproduction (Kairo et al., 2000; Chong et al., 2015). M. hirsutus also injects toxic saliva into the plant during feeding, which results in leaf curling, fruit malformation, bunchy top appearance (Figure 1E) and premature senescence of flowers and foliage (Dufour and Léon, 1997; Chong et al., 2015). Heavy infestations may cause a complete defoliation of the plant, leading to its death (Figure 1F) (Dufour and Léon, 1997; Sagarra and Peterkin, 1999). These impacts have been documented in city parks and gardens in Cyprus (Ülgentürk et al., 2015) and Greece (Milonas and Partsinevelos, 2017). The potential annual economic impact of M. hirsutus to avocado (Persea americana), citrus (Citrus spp.), cotton (Gossypium hirsutum), peanut (Arachis hypogaea), soybean (Glycine max), nursery and vegetable crops was estimated at US$163 million in Florida or US$1.6 billion for the entire United States (Ranjan, 2006). In Egypt, M. hirsutus was reported to cause damage to Albizia lebbek, mulberry, Hibiscus spp., and cotton. In Africa, it was considered as a possible pest of cocoa. In India, Bangladesh and Pakistan it is a pest of cotton, mulberry and several fibre crop species. In India, it has also been considered to be a severe pest of grapes (Muralidharan and Badaya, 2000; Culik et al., 2013). When M. hirsutus was introduced in the Caribbean islands it became a very serious problem. Grenada reported economic losses of $3.5 to $10 million for the season 1996–1997 and Trinidad and Tobago estimated potential losses exceeding $125 million/year, if infestations continued to escalate (Meyerdirk et al., 2001). However, in many countries M. hirsutus is restricted to Hibiscus species and is not a serious pest, possibly because natural enemies effectively reduce its populations (Meyerdirk et al., 2001).

Available measures and their limitations

Are there measures available to prevent pest entry, establishment, spread or impacts such that the risk becomes mitigated? Yes. Although the existing phytosanitary measures identified in Section 3.3.2 do not specifically target M. hirsutus, they mitigate the likelihood of its entry into and spread within the EU (see also Section 3.6.1).

Identification of potential additional measures

Phytosanitary measures (prohibitions) are currently applied to some host plants for planting (see Section 3.3.2). Additional potential risk reduction options and supporting measures are shown in Sections 3.6.1.1 and 3.6.1.2.

Additional potential risk reduction options

Potential additional control measures are listed in Table 6.
Table 6

Selected control measures (a full list is available in EFSA PLH Panel, 2018) for pest entry/establishment/spread/impact in relation to currently unregulated hosts and pathways. Control measures are measures that have a direct effect on pest abundance

Control measure/risk reduction option

(Blue underline = Zenodo doc)

RRO summaryRisk element targeted (entry/establishment/spread/impact)
Growing plants in isolation

Description of possible exclusion conditions that could be implemented to isolate the crop from pests and if applicable relevant vectors. E.g. a dedicated structure such as glass or plastic greenhouses.

Used to mitigate likelihood of infestation by specified pest in vicinity of growing site. Plants could be grown in glass or plastic structures

Entry (reduce contamination/infestation)/spread
Chemical treatments on crops including reproductive materialUsed to mitigate likelihood of infestation of pests susceptible to chemical treatments. Pesticide application for the control of M. hirsutus has been considered to be impractical (Culik et al., 2013). Some neonicotinoid and pyrethroid insecticides (e.g. imidacloprid, thiamethoxam, bifenthrin) as well as their mixture have provided encouraging results regarding the control of the pest (Castle and Prabhaker, 2011; Fatima et al., 2016). However, the use of some neonicotinoids for outdoor use in EU has been banned. Moreover, the natural wax coating covering the various stages of the insect protects it from pesticides (Meyerdirk et al., 2001)Entry/establishment/impact
Chemical treatments on consignments or during processing

Use of chemical compounds that may be applied to plants or to plant products after harvest, during process or packaging operations and storage.

The treatments addressed in this information sheet are:

fumigation;

spraying/dipping pesticides;

surface disinfectants;

process additives;

protective compounds

Used to mitigate likelihood of infestation of pests susceptible to chemical treatments.

Eggs, nymphs and adults of M. hirsutus were susceptible to methyl bromide fumigations. A dose of 48 mg/litre methyl bromide at 21–26°C produced 100% mortality of all life stages (Zettler et al., 2002)

Entry/spread
Physical treatments on consignments or during processing

This information sheet deals with the following categories of physical treatments: irradiation/ionisation; mechanical cleaning (brushing, washing); sorting and grading, and; removal of plant parts (e.g. debarking wood). This information sheet does not address: heat and cold treatment (information sheet 1.14); roguing and pruning (information sheet 1.12).

Used to mitigate likelihood of infestation of pests susceptible to physical treatments

Washing, brushing and other mechanical cleaning methods can be used to reduce the prevalence of the pest in the consignments to be exported or to be planted

Entry/spread
Cleaning and disinfection of facilities, tools and machinery

The physical and chemical cleaning and disinfection of facilities, tools, machinery, transport means, facilities and other accessories (e.g. boxes, pots, pallets, palox, supports, hand tools). The measures addressed in this information sheet are: washing, sweeping and fumigation.

Used to mitigate likelihood of entry or spread of soil borne pests

Entry/spread
Limits on soilUsed to mitigate likelihood of entry or spread of M. hirsutus eggs in soilEntry/spread
Soil treatment

The control of soil organisms by chemical and physical methods listed below:

a) Fumigation; b) Heating; c) Solarisation; d) Flooding; e) Soil suppression; f) Augmentative Biological control; g) Biofumigation

Used to mitigate likelihood of presence of eggs in the soil

Entry/establishment/impact
Heat and cold treatments

Controlled temperature treatments aimed to kill or inactivate pests without causing any unacceptable prejudice to the treated material itself. The measures addressed in this information sheet are: autoclaving; steam; hot water; hot air; cold treatment

Used to mitigate likelihood of infestation of pests susceptible to physical treatments.

Hot water immersion treatment of fruits has been reported as an effective measure for disinfestation of fresh fruits. Effective temperature time combinations for control of M. hirsutus on fruits were 55 min at 47°C, 23 min at 48°C and 13 min at 49°C (Hara and Jacobsen, 2005)

Entry/spread
Controlled atmosphere

Treatment of plants by storage in a modified atmosphere (including modified humidity, O2, CO2, temperature, pressure).

Used to mitigate likelihood of infestation of pests susceptible to modified atmosphere (usually applied during transport) hence to mitigate entry.

Controlled atmosphere storage can be used in commodities such as fresh and dried fruits, flowers and vegetables

Entry/spread (via commodity)
Post‐entry quarantine and other restrictions of movement in the importing country

This information sheet covers post‐entry quarantine (PEQ) of relevant commodities; temporal, spatial and end‐use restrictions in the importing country for import of relevant commodities; Prohibition of import of relevant commodities into the domestic country.

‘Relevant commodities’ are plants, plant parts and other materials that may carry pests, either as infection, infestation, or contamination.

Plants in PEQ are held in conditions that prevent the escape of pests; they can be carefully inspected and tested to verify they are of sufficient plant health status to be released, or may be treated, re‐exported or destroyed. Tests on plants are likely to include laboratory diagnostic assays and bioassays on indicator hosts to check whether the plant material is infected with particular pathogens

Establishment/spread
Selected control measures (a full list is available in EFSA PLH Panel, 2018) for pest entry/establishment/spread/impact in relation to currently unregulated hosts and pathways. Control measures are measures that have a direct effect on pest abundance Control measure/risk reduction option (Blue underline = Zenodo doc) Description of possible exclusion conditions that could be implemented to isolate the crop from pests and if applicable relevant vectors. E.g. a dedicated structure such as glass or plastic greenhouses. Used to mitigate likelihood of infestation by specified pest in vicinity of growing site. Plants could be grown in glass or plastic structures Use of chemical compounds that may be applied to plants or to plant products after harvest, during process or packaging operations and storage. The treatments addressed in this information sheet are: fumigation; spraying/dipping pesticides; surface disinfectants; process additives; protective compounds Used to mitigate likelihood of infestation of pests susceptible to chemical treatments. Eggs, nymphs and adults of M. hirsutus were susceptible to methyl bromide fumigations. A dose of 48 mg/litre methyl bromide at 21–26°C produced 100% mortality of all life stages (Zettler et al., 2002) This information sheet deals with the following categories of physical treatments: irradiation/ionisation; mechanical cleaning (brushing, washing); sorting and grading, and; removal of plant parts (e.g. debarking wood). This information sheet does not address: heat and cold treatment (information sheet 1.14); roguing and pruning (information sheet 1.12). Used to mitigate likelihood of infestation of pests susceptible to physical treatments Washing, brushing and other mechanical cleaning methods can be used to reduce the prevalence of the pest in the consignments to be exported or to be planted The physical and chemical cleaning and disinfection of facilities, tools, machinery, transport means, facilities and other accessories (e.g. boxes, pots, pallets, palox, supports, hand tools). The measures addressed in this information sheet are: washing, sweeping and fumigation. Used to mitigate likelihood of entry or spread of soil borne pests The control of soil organisms by chemical and physical methods listed below: a) Fumigation; b) Heating; c) Solarisation; d) Flooding; e) Soil suppression; f) Augmentative Biological control; g) Biofumigation Used to mitigate likelihood of presence of eggs in the soil Controlled temperature treatments aimed to kill or inactivate pests without causing any unacceptable prejudice to the treated material itself. The measures addressed in this information sheet are: autoclaving; steam; hot water; hot air; cold treatment Used to mitigate likelihood of infestation of pests susceptible to physical treatments. Hot water immersion treatment of fruits has been reported as an effective measure for disinfestation of fresh fruits. Effective temperature time combinations for control of M. hirsutus on fruits were 55 min at 47°C, 23 min at 48°C and 13 min at 49°C (Hara and Jacobsen, 2005) Treatment of plants by storage in a modified atmosphere (including modified humidity, O2, CO2, temperature, pressure). Used to mitigate likelihood of infestation of pests susceptible to modified atmosphere (usually applied during transport) hence to mitigate entry. Controlled atmosphere storage can be used in commodities such as fresh and dried fruits, flowers and vegetables This information sheet covers post‐entry quarantine (PEQ) of relevant commodities; temporal, spatial and end‐use restrictions in the importing country for import of relevant commodities; Prohibition of import of relevant commodities into the domestic country. ‘Relevant commodities’ are plants, plant parts and other materials that may carry pests, either as infection, infestation, or contamination. Plants in PEQ are held in conditions that prevent the escape of pests; they can be carefully inspected and tested to verify they are of sufficient plant health status to be released, or may be treated, re‐exported or destroyed. Tests on plants are likely to include laboratory diagnostic assays and bioassays on indicator hosts to check whether the plant material is infected with particular pathogens

Additional supporting measures

Potential additional supporting measures are listed in Table 7.
Table 7

Selected supporting measures (a full list is available in EFSA PLH Panel, 2018) in relation to currently unregulated hosts and pathways. Supporting measures are organisational measures or procedures supporting the choice of appropriate risk reduction options that do not directly affect pest abundance

Supporting measureRRO summaryRisk element targeted (entry/establishment/spread/impact)
Inspection and trapping

Inspection is defined as the official visual examination of plants, plant products or other regulated articles to determine if pests are present or to determine compliance with phytosanitary regulations (ISPM 5).

The effectiveness of sampling and subsequent inspection to detect pests may be enhanced by including trapping and luring techniques.

Used to mitigate likelihood of infestation by specified pest at origin. Any shipments of fresh plant material from an infested country to another that is not infested should be examined thoroughly to detect M. hirsutus (CABI, 2021)

Establishment/spread
Phytosanitary certificate and plant passport

An official paper document or its official electronic equivalent, consistent with the model certificates of the IPPC, attesting that a consignment meets phytosanitary import requirements (ISPM 5)

a) export certificate (import)

b) plant passport (EU internal trade)

Used to attest which of the above requirements have been applied

Entry/spread
Selected supporting measures (a full list is available in EFSA PLH Panel, 2018) in relation to currently unregulated hosts and pathways. Supporting measures are organisational measures or procedures supporting the choice of appropriate risk reduction options that do not directly affect pest abundance Inspection is defined as the official visual examination of plants, plant products or other regulated articles to determine if pests are present or to determine compliance with phytosanitary regulations (ISPM 5). The effectiveness of sampling and subsequent inspection to detect pests may be enhanced by including trapping and luring techniques. Used to mitigate likelihood of infestation by specified pest at origin. Any shipments of fresh plant material from an infested country to another that is not infested should be examined thoroughly to detect M. hirsutus (CABI, 2021) An official paper document or its official electronic equivalent, consistent with the model certificates of the IPPC, attesting that a consignment meets phytosanitary import requirements (ISPM 5) a) export certificate (import) b) plant passport (EU internal trade) Used to attest which of the above requirements have been applied

Biological or technical factors limiting the effectiveness of measures

M. hirsutus hide in cracks and crevices on the plant bark and in the calyx of fruits, making its detection, especially in early infestations and low population, difficult. The high number of host plants and the wide distribution of M. hirsutus makes the inspections of all consignments imported from countries where the pest occurs difficult. The natural wax coating covering the various stages of M. hirsutus protects it from treatments with contact insecticides.

Uncertainty

Uncertainty exists regarding the suitability of the climate of EU countries in central Europe for the establishment of M. hirsutus. However, its establishment in the southern EU countries is very likely since it has already been detected in Cyprus and Greece (Rhodes). In many countries where climate is suitable, M. hirsutus is not a serious pest, largely due to natural enemies (Kairo et al., 2000), thus there is uncertainty on the magnitude of impact. For example, it is not known if, and how quickly, natural enemies such as the parasitoid Anagyrus kamali, will follow the spread of M. hirsutus in the EU. The presence of M. hirsutus in France and Italy, implied by some interceptions in the USA, is uncertain (Miller et al., 2014). It is likely that the interceptions recorded in the US are on produce imported into the EU from other countries and reexported (see Section 3.2.2).

Conclusions

The criteria assessed by EFSA for consideration of M. hirsutus as a potential EU quarantine pest are met (Table 8).
Table 8

The Panel’s conclusions on the pest categorisation criteria defined in Regulation (EU) 2016/2031 on protective measures against pests of plants (the number of the relevant sections of the pest categorisation is shown in brackets in the first column)

Criterion of pest categorisationPanel’s conclusions against criterion in Regulation (EU) 2016/2031 regarding Union quarantine pestKey uncertainties
Identity of the pest ( 3.1 ) The identity of the pest is established. Taxonomic keys based on morphology of female adults existNone
Absence/presence of the pest in the EU ( 3.2 ) The pest has a restricted distribution in the EU territory (Rhodes Island in Greece and Cyprus)None
Regulatory status ( 3.3 ) Maconellicoccus hirsutus is not regulated as a quarantine pest in the EU; the Cypriot NPPO is taking official actionNone
Pest potential for entry, establishment and spread in the EU ( 3.4 )

Maconellicoccus hirsutus is able to enter into, become established, and spread within the EU territory. The main pathways are:

plants for planting (regulated, some prohibited, some permitted)

fruits, vegetables and cut flowers (regulated, except bananas and pineapple)

None
Potential for consequences in the EU ( 3.5 ) The pests’ introduction could reduce the aesthetic value of various ornamental plants and the production of many cropsIn many countries M. hirsutus is not a serious pest, possibly due to the climate being less favourable, and natural enemies reducing its population levels
Available measures ( 3.6 ) There are measures available to prevent the entry, establishment and spread of M. hirsutus within the EU. Risk reduction options include the inspections and physical treatments on consignments of fresh plant material from infested countries and the production of plants for import into the EU in pest free areas (this could be difficult due to wide distribution of the pest)Eradication and containment actions taken in the Caribbean (for example, restricting the movement of host plant material) were unsuccessful. There is uncertainty regarding how effective risk reduction measures would be in the EU
Conclusion ( 4 ) The criteria assessed by EFSA for consideration as a potential quarantine pest are met
Aspects of assessment to focus on/scenarios to address in future if appropriate Establishment, impact, and natural enemies
The Panel’s conclusions on the pest categorisation criteria defined in Regulation (EU) 2016/2031 on protective measures against pests of plants (the number of the relevant sections of the pest categorisation is shown in brackets in the first column) Maconellicoccus hirsutus is able to enter into, become established, and spread within the EU territory. The main pathways are: plants for planting (regulated, some prohibited, some permitted) fruits, vegetables and cut flowers (regulated, except bananas and pineapple)

Abbreviations

European and Mediterranean Plant Protection Organization Food and Agriculture Organization International Plant Protection Convention International Standards for Phytosanitary Measures Member State EFSA Panel on Plant Health Protected Zone Treaty on the Functioning of the European Union Terms of Reference

Glossary

Application of phytosanitary measures in and around an infested area to prevent spread of a pest (FAO, 2018) Suppression, containment or eradication of a pest population (FAO, 2018) Movement of a pest into an area where it is not yet present, or present but not widely distributed and being officially controlled (FAO, 2018) Application of phytosanitary measures to eliminate a pest from an area (FAO, 2018) Perpetuation, for the foreseeable future, of a pest within an area after entry (FAO, 2018) A walk‐in, static, closed place of crop production with a usually translucent outer shell, which allows controlled exchange of material and energy with the surroundings and prevents release of plant protection products (PPPs) into the environment. The impact of the pest on the crop output and quality and on the environment in the occupied spatial units The entry of a pest resulting in its establishment (FAO, 2018) Any means that allows the entry or spread of a pest (FAO, 2018) Any legislation, regulation or official procedure having the purpose to prevent the introduction or spread of quarantine pests, or to limit the economic impact of regulated non‐quarantine pests (FAO, 2018) A pest of potential economic importance to the area endangered thereby and not yet present there, or present but not widely distributed and being officially controlled (FAO, 2018) A measure acting on pest introduction and/or pest spread and/or the magnitude of the biological impact of the pest should the pest be present. A RRO may become a phytosanitary measure, action or procedure according to the decision of the risk manager Expansion of the geographical distribution of a pest within an area (FAO, 2018)

Appendix A – Maconellicoccus hirsutus host plants/species affected

Source: EPPO Global Database (EPPO, online), García Morales et al. (2016) and other references.

Appendix B – Distribution of Maconellicoccus hirsutus

Distribution records based on EPPO Global Database (EPPO, online) and García Morales et al. (2016).

Appendix C – Import data

Table C.1: Fresh or dried citrus (CN code: 0805) imported in 100 kg into the EU (27) from regions where Maconellicoccus hirsutus is known to occur (Source: Eurostat accessed on 22/9/2021) Table C.2: Cotton linters (CN code: 140420) imported in 100 kg into the EU (27) from regions where Maconellicoccus hirsutus is known to occur (Source: Eurostat accessed on 22/9/2021) Table C.3: Fresh or dried bananas (CN code: 0803) imported in 100 kg into the EU (27) from regions where Maconellicoccus hirsutus is known to occur (Source: Eurostat accessed on 22/9/2021) Table C.4: Fresh grapes (CN code: 080610) imported in 100 kg into the EU (27) from regions where Maconellicoccus hirsutus is known to occur (Source: Eurostat accessed on 22/9/2021) Table C.5: Fresh or dried avocados (CN code: 080440) imported in 100 kg into the EU (27) from regions where Maconellicoccus hirsutus is known to occur (Source: Eurostat accessed on 22/9/2021) Table C.6: Fresh tamarinds, cashew apples, lychees, jackfruit, sapodillo plums, passion fruit, carambola and pitahaya (CN code: 08109020) imported in 100 kg into the EU (27) from regions where Maconellicoccus hirsutus is known to occur (Source: Eurostat accessed on 22/9/2021) Table C.7: Fresh or dried pineapples (CN code: 08043000) imported in 100 kg into the EU (27) from regions where Maconellicoccus hirsutus is known to occur (Source: Eurostat accessed on 19/11/2021)

Is the identity of the pest established, or has it been shown to produce consistent symptoms and/or to be transmissible?

Yes, the identity of the pest is established and Maconellicoccus hirsutus (Green) is the accepted name.

Host statusHost namePlant familyCommon nameReference
Cultivated hosts Abutilon indicum MalvaceaeCountry mallowCABI (2021)
Acalypha hispida EuphorbiaceaeCopperleafCABI (2021)
Aegle marmelos RutaceaeIndian baelChong et al. (2015)
Aglaonema AraceaeAglaonemaChong et al. (2015)
Albizia niopoides FabaceaeGuanacaste, monkey's earringGarcía Morales et al. (2016)
Albizia saman FabaceaeCrow bean tree, monkey podGarcía Morales et al. (2016)
Allamanda ApocynaceaeCABI (2021)
Allamanda cathartica ApocynaceaeYellow allamandaCABI (2021)
Alocasia cucullata AraceaeChinese taroChong et al. (2015)
Alpinia ZingiberaceaeAlpina (ginger and galangal)Chong et al. (2015)
Alpinia purpurata ZingiberaceaeRed gingerCABI (2021)
Althaea MalvaceaeMarshmallowChong et al. (2015)
Amaranthus AmatanthaceaeAmaranthChong et al. (2015)
Abelmoschus esculentus MalvaceaeGumbo, lady's fingers, okraEPPO GD (2021)
Abelmoschus manihot MalvaceaeSunset musk mallow, sunset hibiscus, hibiscus manihotGarcía Morales et al. (2016)
Ananas comosus BromeliaceaePineappleEPPO GD (2021)
Annona AnnonaceaeCABI (2021)
Annona cherimola AnnonaceaeCherimoya, custard apple, graveolaEPPO GD (2021)
Annona muricata AnnonaceaePrickly custard appleEPPO GD (2021)
Annona reticulata AnnonaceaeBullock's heartCABI (2021)
Annona squamosa AnnonaceaeCachiman, Cuban sugar apple, sugar apple, sweetsopEPPO GD (2021)
Anthurium andraeanum AraceaeFlamingo flower, flamingo lily, oilcloth flower, tail flowerEPPO GD (2021)
Arachis hypogaea FabaceaeGroundnut, monkeynut, peanutEPPO GD (2021)
Aralia AraliaceaeCABI (2021)
Artocarpus MoraceaeBreadfruit treesCABI (2021)
Artocarpus altilis MoraceaeBreadfruitCABI (2021)
Asparagus AsparagaceaeCABI (2021)
Asparagus densiflorus LiliaceaeSprenger’s asparagus fernChong et al. (2015)
Asparagus officinalis AsparagaceaeAsparagus, garden asparagus, wild asparagusEPPO GD (2021)
Asparagus setaceus LiliaceaeAsparagus fernCABI (2021)
Averrhoa carambola OxalidaceaeCaramba, carambola, Chinese gooseberry, country gooseberry, star fruitEPPO GD (2021)
Azadirachta indica MeliaceaeNeem treeCABI (2021)
Basella alba BasellaceaeMalabar spinachGarcía Morales et al. (2016)
Bauhinia FabaceaeCamel's footCABI (2021)
Bauhinia variegata FabaceaeMountain ebonyCABI (2021)
Begonia BegoniaceaeBegoniaChong et al. (2015)
Beta ChenopodiaceaeCABI (2021)
Beta vulgaris AmaranthaceaeBeetEPPO GD (2021)
Bignonia BignoniaceaeCABI (2021)
Boehmeria UrticaceaeCABI (2021)
Boehmeria nivea UrticaceaeChina grass, false nettle, ramieEPPO GD (2021)
Bougainvillea NyctaginaceaeCABI (2021)
Bougainvillea NyctaginaceaeBougainvilleaChong et al. (2015)
Bougainvillea spectabilis NyctaginaceaeGreat bougainvilleaChong et al. (2015)
Brassica oleracea BrassicaceaeCabbage, cauliflowerCABI (2021)
Caesalpinia coriaria FabaceaeDivi‐diviChong et al. (2015)
Caesalpinia pulcherrima FabaceaePride‐of‐BarbadosChong et al. (2015)
Cajanus cajan FabaceaeBengal pea, cajan pea, Congo pea, dal, pigeon pea, red gramEPPO GD (2021)
Calliandra Fabaceaestick peaChong et al. (2015)
Callistemon MyrtaceaeBottlebrushChong et al. (2015)
Calostemma AmatanthaceaeWilcannia lilyChong et al. (2015)
Camaesyce (Euphorbia) hypericifolia EuphorbiaceaeGraceful sandmatChong et al. (2015)
Campsis (Tecoma) grandiflora BignoniaceaeChinese trumpet vineChong et al. (2015)
Cananga odorata AnnonaceaeIlang‐ilang (kenanga)Chong et al. (2015)
Capsicum SolanaceaeGarcía Morales et al. (2016)
Capsicum annuum SolanaceaeBell pepper, chilli, paprika, red pepper, sweet pepperEPPO GD (2021)
Capsicum frutescens SolanaceaeBird chilli, bird pepper, cayenne pepper, chilli pepper, hot pepperEPPO GD (2021)
Carica papaya CaricaceaePapaw, papaya, pawpaw, tree melonEPPO GD (2021)
Carissa macrocarpa ApocynaceaeAmatungulu (num‐num)Chong et al. (2015)
Cassia FabaceaeCassiaChong et al. (2015)
Cassia javanica FabaceaeAPPLE BLOSSOM (JAVA CASSIA)Chong et al. (2015)
Casuarina CasuarinaceaeBEEFWOODCABI (2021)
Catharanthus roseus ApocynaceaeMadagascar periwinkleChong et al. (2015)
Ceiba pentandra BombacaceaeKapokCABI (2021)
Celosia argentea AmatanthaceaeCock’s combChong et al. (2015)
Centipede tongavine AraceaeChong et al. (2015)
Ceratonia FabaceaeCABI (2021)
Ceratonia siliqua FabaceaeCarob, carob tree, locust bean, locust tree, St John's breadEPPO GD (2021)
Cestrum nocturnum SolanaceaeNight jessamineChong et al. (2015)
Chrysanthemum AsteraceaeDaisyCABI (2021)
Chrysanthemum coronarium AsteraceaeGarland chrysanthemumCABI (2021)
Chrysothemis pulchella GesneriaceaeSquarestemChong et al. (2015)
Cissus verticillata VitaceaePossum grape vineGarcía Morales et al. (2016)
Citrus RutaceaeEPPO GD (2021)
Citrus aurantiifolia RutaceaeLimeCABI (2021)
Citrus aurantium RutaceaeBigarade, bitter orange, seville orange, sour orangeEPPO GD (2021)
Citrus maxima RutaceaePummeloCABI (2021)
Citrus medica RutaceaeCitronChong et al. (2015)
Citrus nobilis RutaceaeTangorChong et al. (2015)
Citrus paradisi RutaceaeGrapefruit, pomeloEPPO GD (2021)
Citrus reticulata RutaceaeClementine, mandarin, tangerineEPPO GD (2021)
Citrus sinensis Rutaceaesweet orangeEPPO GD (2021)
Clerodendrum aculeatum VerbenaceaeHaggarbushChong et al. (2015)
Clerodendrum infortunatum LamiaceaeCABI (2021)
Codiaeum EuphorbiaceaeCodiaeumChong et al. (2015)
Codiaeum variegatum EuphorbiaceaeGarden crotonCABI (2021)
Coffea RubiaceaeCoffeeCABI (2021)
Coffea arabica RubiaceaeArabian coffeeEPPO GD (2021)
Coffea canephora RubiaceaeCongo coffee, robusta coffeeEPPO GD (2021)
Colubrina arborescens RhamnaceaeGreenheartChong et al. (2015)
Cordyline terminalis LiliaceaeTi plant, palm lilyChong et al. (2015)
Couroupita guianensis LecythidaceaeCannonball treeChong et al. (2015)
Crataegus RosaceaeHawthornChong et al. (2015)
Crescentia cujete BignoniaceaeCalabash treeChong et al. (2015)
Crotalaria FabaceaeCABI (2021)
Croton EuphorbiaceaeCrotonChong et al. (2015)
Cucumis sativus CucurbitaceaeCucumber, gherkinEPPO GD (2021)
Cucurbita CucurbitaceaePumpkinCABI (2021)
Cucurbita maxima CucurbitaceaeGiant pumpkin, marrowEPPO GD (2021)
Cucurbita moschata CucurbitaceaePumpkinCABI (2021)
Cucurbita pepo CucurbitaceaeEdible gourd, garden marrow, pumpkin, summer squashEPPO GD (2021)
Cydonia oblonga RosaceaeQuinceCABI (2021)
Dahlia AsteraceaeCABI (2021)
Delonix regia FabaceaeFlamboyantCABI (2021)
Dendrobium OrchidaceaeDendrobium orchidChong et al. (2015)
Dieffenbachia AraceaeDieffenbachiaChong et al. (2015)
Dimocarpus longan SapindaceaeLonganChong et al. (2015)
Diospyros kaki EbenaceaeChinese date plum, Chinese persimmon, Japanese persimmon, kaki, persimmonEPPO GD (2021)
Dodonaea viscosa SapindaceaeSwitch sorrelCABI (2021)
Dovyalis (Aberia) FlacourtiaceaeCeylon goose berryChong et al. (2015)
Dracaena LiliaceaeDracaena (dragon tree)Chong et al. (2015)
Duranta VerbenaceaeCABI (2021)
Duranta erecta VerbenaceaeGolden dewdropsChong et al. (2015)
Elaeagnus ElaeagnaceaeElaeagnus (oleaster)Chong et al. (2015)
Epipremnum pinnatum AraceaeCentipede tonga vineChong et al. (2015)
Eranthemum pulchellum AcanthaeceaeBlue‐sageChong et al. (2015)
Eriobotrya japonica RosaceaeLoquatChong et al. (2015)
Eryngium foetidum ApiaceaeCulantro, shadow beni, Mexican corianderGarcía Morales et al. (2016)
Erythrina FabaceaeCABI (2021)
Erythrina corallodendron FabaceaeCoral erythrinaChong et al. (2015)
Erythrina crista‐galli FabaceaeCry baby treeChong et al. (2015)
Erythrina spp.FabaceaeCABI (2021)
Erythrina subumbrans FabaceaeDecember treeCABI (2021)
Erythrina variegata FabaceaeFlame tree, Indian coral tree, mountain ebony, tiger's clawEPPO GD (2021)
Euphorbia EuphorbiaceaeSpurgeChong et al. (2015)
Euphorbia pulcherrima EuphorbiaceaeChristmas flower, Christmas star, common poinsettia, lobster plant, Mexican flame‐leaf, painted leaf, poinsettiaEPPO GD (2021)
Ficus MoraceaeCABI (2021)
Ficus benghalensis MoraceaeBanyanCABI (2021)
Ficus benjamina MoraceaeBenjamin's fig, Java fig, small‐leaved rubber plant, tropical laurel, weeping fig, Benjamin treeEPPO GD (2021)
Ficus carica MoraceaeCommon fig, edible figEPPO GD (2021)
Ficus elastica MoraceaeRubber plantCABI (2021)
Ficus laurifolia MoraceaeCABI (2021)
Ficus obtusifolia MoraceaeCABI (2021)
Ficus pertusa MoraceaeCABI (2021)
Ficus platyphylla MoraceaeCABI (2021)
Ficus pumila MoraceaeCreeping figCABI (2021)
Ficus racemosa MoraceaeCluster treeCABI (2021)
Ficus religiosa MoraceaeSacred fig treeCABI (2021)
Ficus semicordata MoraceaeCABI (2021)
Flacourtis indica FlacourtiaceaeGovernor’s plumChong et al. (2015)
Gerbera AsteraceaeGerberaChong et al. (2015)
Glebionis coronaria AsteraceaeGarland chrysanthemum, chrysanthemum greens, edible chrysanthemumGarcía Morales et al. (2016)
Gliricidia sepium FabaceaeGliricidiaCABI (2021)
Glycine max FabaceaeSoybeanEPPO GD (2021)
Glycosmis pentaphylla RutaceaeOrange berry, gin berryGarcía Morales et al. (2016)
Cocos nucifera ArecaceaeCommon coconut palmEPPO GD (2021)
Colocasia AraceaeCABI (2021)
Colocasia esculenta AraceaeChinese potato, cocoyam, dasheen, eddoe, Egyptian colocasia, elephant's‐ear, kalo, taro, wild taro, yamEPPO GD (2021)
Gossypium MalvaceaeCottonCABI (2021)
Gossypium arboreum MalvaceaeCotton, treeCABI (2021)
Gossypium herbaceum MalvaceaeShort staple cottonCABI (2021)
Gossypium hirsutum MalvaceaeAmerican upland cotton, upland cottonEPPO GD (2021)
Grevillea ProteaceaeCABI (2021)
Grevillea robusta ProteaceaeSilk oakChong et al. (2015)
Hamelia RubiaceaeHamelia (firebush)Chong et al. (2015)
Helianthus annuus AsteraceaeCommon sunflower, sunflowerEPPO GD (2021)
Hevea EuphorbiaceaeGarcía Morales et al. (2016)
Hevea brasiliensis EuphorbiaceaeBrazilian rubber tree, para rubber, para rubber treeEPPO GD (2021)
Hibiscus boryanus MalvaceaeGarcía Morales et al. (2016)
Hibiscus MalvaceaeRose mallowsCABI (2021)
Hibiscus acetosella MalvaceaeAfrican rosemallowChong et al. (2015)
Hibiscus cannabinus MalvaceaeBombay hemp, Deccan hemp, kenafEPPO GD (2021)
Hibiscus elatus MalvaceaeBlue mahoeCABI (2021)
Hibiscus manihot MalvaceaeBeleCABI (2021)
Hibiscus mutabilis MalvaceaeCotton roseCABI (2021)
Hibiscus rosa‐sinensis MalvaceaeChina rose, Chinese hibiscus, Chinese rose, Hawaiian hibiscus, rose mallow, rose of China, shoe‐black plant, shoe‐flowerEPPO GD (2021)
Hibiscus sabdariffa MalvaceaeJamaica sorrel, red sorrel, roselle, tropical cranberryEPPO GD (2021)
Hibiscus schizopetalus MalvaceaeFringed hibiscusCABI (2021)
Hibiscus surattensis MalvaceaeCABI (2021)
Hibiscus syriacus MalvaceaeShrubby althaeaCABI (2021)
Hibiscus tiliaceus MalvaceaeCoast hibiscus, hau tree, linden hibiscus, mahoe, mahoe tree, wild cotton treeEPPO GD (2021)
Holmskioldia sanguinea VerbenaceaeChinese hatplantChong et al. (2015)
Jacaranda BignoniaceaeCABI (2021)
Jacaranda mimusifolia BignoniaceaeBlack pouiChong et al. (2015)
Jasminum OleaceaeJasmineCABI (2021)
Jasminum sambac OleaceaeArabian jasmineCABI (2021)
Kalanchoe CrassulaceaeWidow’s‐thrillChong et al. (2015)
Kigelia BignoniaceaeSausage treeChong et al. (2015)
Lactuca sativa AsteraceaeGarden lettuce, lettuceEPPO GD (2021)
Lagerstroemia speciosa LythraceaePride of IndiaChong et al. (2015)
Lantana VerbenaceaeLantanaChong et al. (2015)
Lantana camara VerbenaceaeLantanaCABI (2021)
Leonotis LamiaceaeLion’s earChong et al. (2015)
Manihot esculenta EuphorbiaceaeCassava, manioc, tapiocaEPPO GD (2021)
Mangifera AnacardiaceaeCABI (2021)
Mangifera indica AnacardiaceaeMangoEPPO GD (2021)
Manilkara zapota SapotaceaeBully tree, chapoti, chicle, chiku, marmalade plum, noseberry, sapodilla, sapodilla plum, sapotaEPPO GD (2021)
Malpighia glabra MalpighiaceaeBarbados cherryEPPO GD (2021)
Malus domestica RosaceaeAppleEPPO GD (2021)
Malus sylvestris RosaceaeCrab apple, wild apple, wild crabEPPO GD (2021)
Malvaviscus arboreus MalvaceaeWax mallowCABI (2021)
Medicago sativa FabaceaeLucerneCABI (2021)
Melia azedarach MeliaceaeChinaberry treeChong et al. (2015)
Melicocca bijugatus SapindaceaeSpanish limeChong et al. (2015)
Mimosa FabaceaeSensitive plantsCABI (2021)
Mimosa caesalpiniifolia FabaceaeEPPO GD (2021)
Mimosa diplotricha FabaceaeCreeping‐sensitive plantCABI (2021)
Mimosa hostilis FabaceaeEPPO GD (2021)
Mimosa pigra FabaceaeGiant sensitive plantCABI (2021)
Mimosa pudica FabaceaeSensitive plantCABI (2021)
Morus MoraceaeMulberry treeCABI (2021)
Morus alba MoraceaeSilkworm mulberry, white mulberryEPPO GD (2021)
Morus nigra L.MoraceaeBlack mulberryChong et al. (2015)
Murraya exotica RutaceaeChinese box, orange jessamineChong et al. (2015)
Murraya koenigii RutaceaeCurry leaf, karapinchaEPPO GD (2021)
Murraya paniculata RutaceaeOrange jasmine, orange jessamine, china box, mock orangeGarcía Morales et al. (2016)
Musa MusaceaeBananaCABI (2021)
Musa paradisiaca MusaceaePlantainCABI (2021)
Mussaenda RubiaceaeCABI (2021)
Myrtus communis MyrtaceaeMyrtleCABI (2021)
Nephrolepis biserrata DryopteridaceaeGiant swordfernChong et al. (2015)
Nephrolepis exaltata DryopteridaceaeBoston swordfernChong et al. (2015)
Nerium oleander ApocynaceaeCommon oleander, oleander, rose bayEPPO GD (2021)
Pachystachys lutea AcanthaeceaePachystachys, lollipop‐plantChong et al. (2015)
Passiflora PassifloraceaePassionflowerCABI (2021)
Passiflora caerulea PassifloraceaeBluecrown passionflowerChong et al. (2015)
Passiflora edulis PassifloraceaePassionfruitCABI (2021)
Passiflora quadrangularis PassifloraceaeGiant granadillaChong et al. (2015)
Pavonia MalvaceaeSwampmallowChong et al. (2015)
Peperomia pellucid PiperaceaeMan‐to‐ManChong et al. (2015)
Pereskia bleo CactaceaeRose cactusChong et al. (2015)
Persea americana LauraceaeAlligator pear, avocado, avocado pear, holly ghost pearEPPO GD (2021)
Petrea volubilis VerbenaceaeQueen’s‐wreathChong et al. (2015)
Phaseolus vulgaris FabaceaeBush bean, climbing French bean, climbing kidney bean, field bean, flageolet bean, French bean, garden bean, green bean, haricot bean, kidney bean, pop bean, snap bean, string beanEPPO GD (2021)
Philodendron AraceaePhilodendronChong et al. (2015)
Phoenix dactylifera ArecaceaeCommon date palm, date palmEPPO GD (2021)
Phoenix sylvestris ArecaceaeEast Indian wine palm, silver date palm, wild date palmEPPO GD (2021)
Phyllanthus acidus EuphorbiaceaeTahitian gooseberry treeChong et al. (2015)
Phyllanthus elsiae EuphorbiaceaeCABI (2021)
Phyllanthus niruri EuphorbiaceaeSeed‐under‐the‐leafCABI (2021)
Plumbago auriculata PlumbaginaceaeCape leadwortChong et al. (2015)
Portulaca grandiflora PortulacaceaeRose mossCABI (2021)
Portulaca oleracea PortulacaceaeCommon purslane, duckweed, little hogweed, pursleyGarcía Morales et al. (2016)
Portulaca pilosa PortulacaceaeKiss‐me‐quick, rimson‐flowered purslane, hairy pigweed, pink purslane, shaggy portulacaGarcía Morales et al. (2016)
Prunus armeniaca RosaceaeApricotEPPO GD (2021)
Prunus domestica RosaceaeEuropean plum, garden plum, plumEPPO GD (2021)
Prunus persica RosaceaePeachEPPO GD (2021)
Prunus salicina RosaceaeJapanese plumCABI (2021)
Psidium MyrtaceaeGuavaCABI (2021)
Psidium guajava MyrtaceaeCommon guava, guava, yellow guavaEPPO GD (2021)
Punica granatum LythraceaePomegranateEPPO GD (2021)
Pyrus communis RosaceaeCommon pear, pearEPPO GD (2021)
Quercus FagaceaeOakChong et al. (2015)
Rhododendron EricaceaeAzaleaCABI (2021)
Ricinus communis EuphorbiaceaeCastor‐oil plant, castor beanEPPO GD (2021)
Rivina humilis PhytolacaceaeRougeplantChong et al. (2015)
Robinia pseudoacacia FabaceaeBlack locustCABI (2021)
Rosa RosaceaeRoseChong et al. (2015)
Russelia equisetiformis ScrophulariaceaeFountainbushChong et al. (2015)
Saccharum officinarum PoaceaeSugarcaneCABI (2021)
Salix SalicaceaeWillowsCABI (2021)
Schefflera AraliaceaeScheffleraChong et al. (2015)
Senna FabaceaeSennaChong et al. (2015)
Senna siamea FabaceaeYellow cassiaCABI (2021)
Solanum aethiopicum SolanaceaeAfrican scarlet eggplantCABI (2021)
Solanum bicolor SolanaceaeChong et al. (2015)
Solanum lycopersicum SolanaceaeTomatoEPPO GD (2021)
Solanum melongena SolanaceaeAubergine, eggplantEPPO GD (2021)
Spondias dulcis AnacardiaceaeOtaheite appleCABI (2021)
Spondias purpurea AnacardiaceaeRed mombin, purple mombinCABI (2021)
Stachytarpheta jamaicensis VerbenaceaeLight‐blue snakeweedChong et al. (2015)
Syngonium podophyllum AraceaeAmerican evergreenChong et al. (2015)
Syzygium cumini MyrtaceaeBlack plumCABI (2021)
Syzygium malaccense MyrtaceaeMalaysian appleChong et al. (2015)
Tabebuia BignoniaceaeTrumpet‐treeChong et al. (2015)
Tabebuia heterophylla BignoniaceaePink trumpet treeCABI (2021)
Tamarindus indica FabaceaeTamarindChong et al. (2015)
Tamarix TamaricaceaeTamariskCABI (2021)
Tecoma capensis BignoniaceaeCape honeysuckleChong et al. (2015)
Tecoma stans BignoniaceaeYellow trumpetbushChong et al. (2015)
Terminalia catappa CombretaceaeSingapore almondCABI (2021)
Theobroma bicolor MalvaceaeBacao, Nicaraguan cocoaEPPO GD (2021)
Theobroma cacao MalvaceaeCacao, cocoa, common cacao, common cocoaEPPO GD (2021)
Theobroma grandiflorum MalvaceaeCupuassuEPPO GD (2021)
Thunbergia erecta AcanthaeceaeBush clockvineChong et al. (2015)
Vinca minor ApocynaceaeCommon periwinkle, vincaChong et al. (2015)
Vitis VitaceaeRapeCABI (2021)
Vitis vinifera VitaceaeCommon grapevine, grapevine, European grapeEPPO GD (2021)
Zea mays PoaceaeMaizeCABI (2021)
Ziziphus RhamnaceaeCABI (2021)
Ziziphus RhamnaceaeJujubeChong et al. (2015)
Ziziphus jujuba RhamnaceaeCommon jujubeCABI (2021)
Ziziphus mauritiana RhamnaceaeIndian jujubeEPPO GD (2021)
Ziziphus mucronata RhamnaceaeCABI (2021)
Ziziphus spina‐christi RhamnaceaeChrist's thorn jujubeCABI (2021)
Wild weed hosts Abutilon fruticosum MalvaceaeTexas Indian mallow, pelotazo, sweet Indian mallowGarcía Morales et al. (2016)
Acacia FabaceaeWattlesCABI (2021)
Acacia acatlensis FabaceaeCABI (2021)
Acacia cochliacantha FabaceaeCABI (2021)
Acacia farnesiana FabaceaeHuisacheCABI (2021)
Acacia hindsii FabaceaeCABI (2021)
Acacia nilotica FabaceaeGum arabic treeCABI (2021)
Acalypha EuphorbiaceaeCopperleafCABI (2021)
Acalypha indica EuphorbiaceaeIndian acalypha, Indian mercury, Indian copperleaf, Indian nettle, Three‐seeded mercuryGarcía Morales et al. (2016)
Acalypha wilkesiana EuphorbiaceaeCopperleaf and Jacob’s coatGarcía Morales et al. (2016)
Acanthus ilicifolius AcanthaceaeCopperleafCABI (2021)
Acharia LimacodidaeCABI (2021)
Achyranthes aspera AmaranthaceaeDevil's horsewhipCABI (2021)
Acokanthera ApocynaceaeGarcía Morales et al. (2016)
Aegiphila martinicensis LamiaceaeCABI (2021)
Albizia FabaceaeCABI (2021)
Albizia lebbeck FabaceaeIndian sirisCABI (2021)
Angelica ApiaceaeCABI (2021)
Anthurium AraceaeCABI (2021)
Bauhinia forficata FabaceaeBrazilian orchid treeGarcía Morales et al. (2016)
Bauhinia racemosa FabaceaeGarcía Morales et al. (2016)
Bauhinia vahlii FabaceaeGarcía Morales et al. (2016)
Biancaea decapetala FabaceaeShoofly, Mauritius, Mysore thornGarcía Morales et al. (2016)
Bidens pilosa AsteraceaeBeggar tick, bur marigold, butterfly needlesGarcía Morales et al. (2016)
Blighia sapida SapindaceaeAkeeChong et al. (2015)
Byttneria aculeata MalvaceaeCABI (2021)
Calathea warszewiczii MarantaceaeGarcía Morales et al. (2016)
Calophyllum CalophyllaceaeGarcía Morales et al. (2016)
Carissa bispinosa ApocynaceaeGarcía Morales et al. (2016)
Cassia glauca FabaceaeGarcía Morales et al. (2016)
Cassia renigera FabaceaeGarcía Morales et al. (2016)
Cedrela odorata MeliaceaeSpanish cedarCABI (2021)
Centrolobium paraense FabaceaeEPPO GD (2021)
Chenopodium album AmaranthaceaeGoosefoot, green pigweed, lamb's quarters, wild spinach, fat‐hen, white goosefoot, pigweedEPPO GD (2021)
Clitoria ternatea FabaceaeButterfly‐peaCABI (2021)
Coccoloba uvifera PolygonaceaeJamaica kino, platter leaf, sea grape, common sea grapeEPPO GD (2021)
Combretum CombretaceaeGarcía Morales et al. (2016)
Corchorus TiliaceaeJutesCABI (2021)
Corchorus capsularis TiliaceaeWhite juteCABI (2021)
Corchorus olitorius TiliaceaeJuteCABI (2021)
Cordia curassavica BoraginaceaeBlack sage or wild sageGarcía Morales et al. (2016)
Cordia dichotoma BoraginaceaeIndian cherryCABI (2021)
Cordyline fruticosa AsparagaceaeBongbush, cabbage palm, kiwi, palm lily, ti‐palmGarcía Morales et al. (2016)
Cosmos AsteraceaeEPPO GD (2021)
Crotalaria micans FabaceaeCABI (2021)
Croton flavens EuphorbiaceaeGarcía Morales et al. (2016)
Cyperus CyperaceaeGarcía Morales et al. (2016)
Dalbergia FabaceaeRosewoodsCABI (2021)
Datura SolanaceaeJimsonweed (angel trumpet)Chong et al. (2015)
Daucus carota ApiaceaeQueen Anne’s laceChong et al. (2015)
Desmanthus virgatus FabaceaeFalse tamarindCABI (2021)
Dioscorea DioscoreaceaeGarcía Morales et al. (2016)
Emilia AsteraceaeGarcía Morales et al. (2016)
Enterolobium FabaceaeCABI (2021)
Enterolobium cyclocarpum FabaceaeEar pod treeCABI (2021)
Epipremnum aureum AraceaeGolden pothos, Ceylon creeper, Hunter's robe, ivy arumGarcía Morales et al. (2016)
Erythrina resinifera FabaceaeGarcía Morales et al. (2016)
Erythrina speciosa FabaceaeGarcía Morales et al. (2016)
Erythrina vespertilio FabaceaeGarcía Morales et al. (2016)
Eugenia uniflora MyrtaceaeSurinam cherryCABI (2021)
Euphorbia atoto CABI (2021)
Euphorbia hypericifolia EuphorbiaceaeGraceful spurge, golden spurge, and chickenweedGarcía Morales et al. (2016)
Ficus amplissima MoraceaeIndian Bat tree, Indian Bat fig, PimpriGarcía Morales et al. (2016)
Ficus lacor MoraceaeGarcía Morales et al. (2016)
Flacourtia indica FlacourtiaceaeGovernor's plumGarcía Morales et al. (2016)
Gliricidia FabaceaeCABI (2021)
Gliricidia maculata FabaceaeCABI (2021)
Grevillea robusta ProteaceaeAustralian silky oak, silk oak, silk‐bark oak, silky oakEPPO GD (2021)
Grewia TiliaceaeCABI (2021)
Guazuma ulmifolia SterculiaceaeBastard cedarCABI (2021)
Gymnanthemum urticifolium AsteraceaeGarcía Morales et al. (2016)
Haldina cordifolia RubiaceaeHeart‐leaf adinaGarcía Morales et al. (2016)
Heliconia HeliconiaceaeEPPO GD (2021)
Hoya carnosa AsclepiadaceaeWax plantCABI (2021)
Inga FabaceaeGarcía Morales et al. (2016)
Inga edulis FabaceaeFood inga, icecream bean, St John's breadEPPO GD (2021)
Inga ingoides FabaceaeCABI (2021)
Inga vera FabaceaeCABI (2021)
Ipomoea ConvolvulaceaeMorning gloryCABI (2021)
Ipomoea batatas ConvolvulaceaeSweet potatoEPPO GD (2021)
Ixora RubiaceaeEPPO GD (2021)
Ixora chinensis RubiaceaeFlame of the woods, jungle flame, jungle geraniumEPPO GD (2021)
Jatropha curcas EuphorbiaceaeBarbados nut, purging nut, physic nutEPPO GD (2021)
Laportea aestuans UrticaceaeWest Indian woodnettleGarcía Morales et al. (2016)
Lawsonia LythraceaeGarcía Morales et al. (2016)
Lawsonia inermis LythraceaeEgyptian privetCABI (2021)
Leonotis nepetifolia LamiaceaeChristmas candlestickGarcía Morales et al. (2016)
Leucaena FabaceaeCABI (2021)
Leucaena leucocephala FabaceaeLeucaenaCABI (2021)
Lithocarpus FagaceaeStone oakChong et al. (2015)
Macaranga EuphorbiaceaeCABI (2021)
Malachra alceifolia MalvaceaeCABI (2021)
Malpighia MalpighiaceaeCABI (2021)
Malpighia emarginata MalpighiaceaeCABI (2021)
Malvaviscus conzattii MalvaceaeCABI (2021)
Miconia cornifolia MelastomataceaeGarcía Morales et al. (2016)
Mikania cordata AsteraceaeGarcía Morales et al. (2016)
Mimosa tenuiflora FabaceaeGarcía Morales et al. (2016)
Momordica charantia CucurbitaceaeBitter gourdCABI (2021)
Montanoa grandiflora AsteraceaeCABI (2021)
Mussaenda erythrophylla RubiaceaeAshanti blood, red flag bush, red flag mussaendaEPPO GD (2021)
Nephelium lappaceum SapindaceaeRambutanEPPO GD (2021)
Nerium indicum ApocynaceaeGarcía Morales et al. (2016)
Opuntia CactaceaeEPPO GD (2021)
Paritium MalvaceaeGarcía Morales et al. (2016)
Parkinsonia aculeata FabaceaeMexican palo‐verdeCABI (2021)
Parthenium hysterophorus AsteraceaeParthenium weedCABI (2021)
Persea LauraceaeCABI (2021)
Petiveria alliacea PhytolaccaceaeGarcía Morales et al. (2016)
Phyllanthus amarus EuphorbiaceaeGale of the wind, carry me seed, seed on the leafGarcía Morales et al. (2016)
Phyllanthus urinaria EuphorbiaceaeLeafflowerGarcía Morales et al. (2016)
Piper tuberculatum PiperaceaeGarcía Morales et al. (2016)
Pithecellobium FabaceaeCABI (2021)
Pithecellobium caribaeum FabaceaeGarcía Morales et al. (2016)
Plerandra elegantissima AraliaceaeFalse aralia
Prosopis FabaceaeCABI (2021)
Prosopis cineraria FabaceaeScrew‐beanCABI (2021)
Prosopis laevigata FabaceaeCABI (2021)
Quisqualis CombretaceaeCABI (2021)
Rosa obtusifolia RosaceaeGarcía Morales et al. (2016)
Samanea saman FabaceaeRain treeCABI (2021)
Schefflera actinophylla AraliaceaeOctopus tree, Queensland umbrella tree, star leaf, umbrella treeEPPO GD (2021)
Schefflera pueckleri AraliaceaeMallet flowerGarcía Morales et al. (2016)
Schinus molle AnacardiaceaeFalse pepper treeGarcía Morales et al. (2016)
Schinus terebinthifolia AnacardiaceaeBrazilian pepper treeGarcía Morales et al. (2016)
Scoparia dulcis PlantaginaceaeLicorice weed, goat weed, scoparia‐weed, sweet‐broomGarcía Morales et al. (2016)
Senna italica FabaceaeSenegal sennaGarcía Morales et al. (2016)
Senna obtusifolia FabaceaeSicklepodGarcía Morales et al. (2016)
Senna polyphylla FabaceaeGarcía Morales et al. (2016)
Senna sulfurea FabaceaeGarcía Morales et al. (2016)
Senna surattensis FabaceaeGolden senna, foetid cassia, glaucous cassia, glossy showerGarcía Morales et al. (2016)
Sesbania sesban FabaceaeSesban, common sesban, Egyptian pea, Egyptian rattle podGarcía Morales et al. (2016)
Sida acuta MalvaceaeSidaCABI (2021)
Solandra SolanaceaeCABI (2021)
Solanum americanum SolanaceaeEastern black nightshade, glossy nightshade, West Indian nightshade, American black nightshadeEPPO GD (2021)
Solanum donianum SolanaceaeGarcía Morales et al. (2016)
Solanum umbellatum SolanaceaeCABI (2021)
Spondias AnacardiaceaePurple mombinCABI (2021)
Spondias mombin AnacardiaceaeGolden apple, hog‐plum tree, yellow mombinEPPO GD (2021)
Spondias tuberosa AnacardiaceaeImbuEPPO GD (2021)
Synedrella nodiflora AsteraceaeSynedrellaGarcía Morales et al. (2016)
Syzygium aqueum MyrtaceaeWater appleGarcía Morales et al. (2016)
Syzygium aromaticum MyrtaceaeCloveCABI (2021)
Tabernaemontana divaricata ApocynaceaeGarcía Morales et al. (2016)
Talinum paniculatum TalinaceaeFame flower, Jewels‐of‐Opar, pink baby‐breathEPPO GD (2021)
Talipariti elatum MalvaceaeBlue mahoeGarcía Morales et al. (2016)
Tamarindus FabaceaeCABI (2021)
Tectona grandis LamiaceaeCommon teakEPPO GD (2021)
Templetonia FabaceaeGarcía Morales et al. (2016)
Tephrosia FabaceaeHoary‐peaCABI (2021)
Teramnus labialis FabaceaeBlue wissCABI (2021)
Terminalia CombretaceaeGarcía Morales et al. (2016)
Terminalia mantaly CombretaceaeCABI (2021)
Terminalia neotaliala CombretaceaeMadagascar almond treeGarcía Morales et al. (2016)
Tetracera DilleniaceaeCABI (2021)
Theobroma speciosum MalvaceaeEPPO GD (2021)
Thespesia MalvaceaeCABI (2021)
Thespesia lampas MalvaceaeCABI (2021)
Thespesia populnea MalvaceaePortia treeCABI (2021)
Tithonia diversifolia AsteraceaeMexican sunflowerCABI (2021)
Tradescantia CommelinaceaeGarcía Morales et al. (2016)
Trema micrantha CannabaceaeJamaican nettle tree, capulinGarcía Morales et al. (2016)
Vachellia nilotica FabaceaeGum arabic tree, babul, thorn mimosa, Egyptian acacia, thorny acaciaGarcía Morales et al. (2016)
Verbesina fastigiata AsteraceaeCABI (2021)
Viburnum odoratissimum CaprifoliaceaeSweet viburnumGarcía Morales et al. (2016)
Vigna mungo FabaceaeBlack gramGarcía Morales et al. (2016)
Vigna unguiculata FabaceaeCowpeaGarcía Morales et al. (2016)
Volkameria aculeata LamiaceaeGarcía Morales et al. (2016)
Xanthosoma AraceaeCocoyamCABI (2021)
Zinnia AsteraceaeCABI (2021)
RegionCountrySub‐national (e.g. State)StatusReference
North AmericaMexicoPresent, restricted distributionEPPO GD (2021)
USAPresent, restricted distributionEPPO GD (2021)
USAAlabamaPresent, no detailsEPPO GD (2021)
USACaliforniaPresent, restricted distributionEPPO GD (2021)
USAFloridaPresent, few occurrencesEPPO GD (2021)
USAGeorgiaPresent, few occurrencesEPPO GD (2021)
USALouisianaPresent, no detailsEPPO GD (2021)
USANew YorkPresent, no detailsEPPO GD (2021)
USANorth CarolinaPresent, no detailsEPPO GD (2021)
USAOklahomaPresent, no detailsEPPO GD (2021)
USASouth CarolinaPresent, no detailsEPPO GD (2021)
USATennesseePresent, no detailsEPPO GD (2021)
USATexasPresent, no detailsGarcía Morales et al. (2016)
Central AmericaBelizePresent, no detailsEPPO GD (2021)
Costa RicaPresent, restricted distributionEPPO GD (2021)
GuatemalaAbsent, unreliable recordEPPO GD (2021)
NicaraguaPresent, restricted distributionEPPO GD (2021)
CaribbeanAnguillaAbsent, unreliable recordEPPO GD (2021)
Antigua and BarbudaPresent, no detailsEPPO GD (2021)
ArubaPresent, no detailsEPPO GD (2021)
BahamasPresent, no detailsEPPO GD (2021)
BarbadosPresent, no detailsEPPO GD (2021)
Cayman IslandsPresent, no detailsEPPO GD (2021)
CubaPresent, no detailsGarcía Morales et al. (2016)
DominicaPresent, no detailsEPPO GD (2021)
Dominican RepublicAbsent, unreliable recordEPPO GD (2021)
GrenadaPresent, restricted distributionEPPO GD (2021)
GuadeloupePresent, no detailsEPPO GD (2021)
HaitiPresent, widespreadEPPO GD (2021)
JamaicaPresent, few occurrencesEPPO GD (2021)
MartiniquePresent, no detailsEPPO GD (2021)
MontserratPresent, no detailsEPPO GD (2021)
Netherlands AntillesPresent, no detailsEPPO GD (2021)
Puerto RicoPresent, no detailsEPPO GD (2021)
Saint LuciaPresent, no detailsEPPO GD (2021)
St Kitts‐NevisPresent, no detailsEPPO GD (2021)
St Vincent and the GrenadinesPresent, no detailsEPPO GD (2021)
Saint BarthelemyPresent, no detailsGarcía Morales et al. (2016)
Saint MartinPresent, no detailsGarcía Morales et al. (2016)
Trinidad and TobagoPresent, no detailsEPPO GD (2021)
Virgin Islands (British)Present, no detailsEPPO GD (2021)
Virgin Islands (US)Present, no detailsEPPO GD (2021)
South AmericaBrazilPresent, restricted distributionEPPO GD (2021)
BrazilAlagoasPresent, no detailsEPPO GD (2021)
BrazilBahiaPresent, restricted distributionEPPO GD (2021)
BrazilEspirito SantoPresent, restricted distributionEPPO GD (2021)
BrazilMaranhaoPresent, no detailsEPPO GD (2021)
BrazilMato GrossoPresent, no detailsEPPO GD (2021)
BrazilParaPresent, no detailsEPPO GD (2021)
BrazilPernambucoPresent, no detailsEPPO GD (2021)
BrazilRio Grande do SulPresent, no detailsEPPO GD (2021)
BrazilRoraimaPresent, restricted distributionEPPO GD (2021)
BrazilSanta CatarinaPresent, no detailsEPPO GD (2021)
BrazilSao PauloPresent, no detailsEPPO GD (2021)
ColombiaPresent, restricted distributionEPPO GD (2021)
French GuianaPresent, no detailsEPPO GD (2021)
GuyanaPresent, widespreadEPPO GD (2021)
SurinamePresent, restricted distributionEPPO GD (2021)
VenezuelaPresent, no detailsEPPO GD (2021)
EU (27)CyprusPresent, widespreadEPPO GD (2021)
GreecePresent, restricted distributionEPPO GD (2021)
AfricaAlgeriaAbsent, invalid recordEPPO GD (2021)
BeninPresent, no detailsEPPO GD (2021)
Burkina FasoPresent, no detailsEPPO GD (2021)
CameroonPresent, no detailsEPPO GD (2021)
Central African RepublicPresent, no detailsEPPO GD (2021)
ChadPresent, no detailsEPPO GD (2021)
CongoPresent, no detailsEPPO GD (2021)
Congo, Democratic republic of thePresent, no detailsEPPO GD (2021)
Cote d'IvoirePresent, no detailsEPPO GD (2021)
EgyptPresent, no detailsEPPO GD (2021)
GabonPresent, no detailsEPPO GD (2021)
GambiaPresent, no detailsEPPO GD (2021)
KenyaPresent, no detailsEPPO GD (2021)
LiberiaPresent, no detailsEPPO GD (2021)
NigerPresent, no detailsEPPO GD (2021)
NigeriaPresent, no detailsEPPO GD (2021)
ReunionPresent, no detailsEPPO GD (2021)
SenegalPresent, no detailsEPPO GD (2021)
SeychellesPresent, no detailsEPPO GD (2021)
Socotra IslandPresent, no detailsGarcía Morales et al. (2016)
SomaliaPresent, no detailsEPPO GD (2021)
SudanPresent, no detailsEPPO GD (2021)
TanzaniaPresent, no detailsEPPO GD (2021)
TunisiaPresent, restricted distributionEPPO GD (2021)
ZambiaAbsent, invalid recordEPPO GD (2021)
ZairePresent, no detailsGarcía Morales et al. (2016)
ZanzibarPresent, no detailsGarcía Morales et al. (2016)
AsiaBaliPresent, no detailsGarcía Morales et al. (2016)
BangladeshPresent, no detailsEPPO GD (2021)
Brunei DarussalamPresent, no detailsEPPO GD (2021)
CambodiaPresent, no detailsEPPO GD (2021)
ChinaPresent, restricted distributionEPPO GD (2021)
ChinaAomen (Macau)Present, no detailsEPPO GD (2021)
ChinaGuangdongPresent, no detailsEPPO GD (2021)
ChinaGuangxiPresent, no detailsGarcía Morales et al. (2016)
ChinaShanxiPresent, no detailsEPPO GD (2021)
ChinaXianggang (Hong Kong)Present, no detailsEPPO GD (2021)
ChinaXizhangPresent, no detailsEPPO GD (2021)
ChinaYunnanPresent, no detailsEPPO GD (2021)
ChinaHong KongPresent, no detailsGarcía Morales et al. (2016)
IndiaPresent, widespreadEPPO GD (2021)
IndiaAndaman and Nicobar IslandsPresent, no detailsEPPO GD (2021)
IndiaAndhra PradeshPresent, no detailsEPPO GD (2021)
IndiaAssamPresent, no detailsEPPO GD (2021)
IndiaBiharPresent, no detailsEPPO GD (2021)
IndiaDelhiPresent, no detailsEPPO GD (2021)
IndiaGujaratPresent, no detailsEPPO GD (2021)
IndiaKarnatakaPresent, no detailsEPPO GD (2021)
IndiaKeralaPresent, no detailsEPPO GD (2021)
IndiaMadhya PradeshPresent, no detailsEPPO GD (2021)
IndiaMaharashtraPresent, no detailsEPPO GD (2021)
IndiaOdishaPresent, no detailsEPPO GD (2021)
IndiaPunjabPresent, no detailsEPPO GD (2021)
IndiaTamil NaduPresent, no detailsEPPO GD (2021)
IndiaTelanganaPresent, no detailsEPPO GD (2021)
IndiaTripuraPresent, no detailsEPPO GD (2021)
IndiaUttar PradeshPresent, no detailsEPPO GD (2021)
IndiaWest BengalPresent, no detailsEPPO GD (2021)
IndonesiaPresent, widespreadEPPO GD (2021)
IndonesiaFloresPresent, no detailsGarcía Morales et al. (2016)
IndonesiaIrian JayaPresent, no detailsEPPO GD (2021)
IndonesiaJavaPresent, no detailsEPPO GD (2021)
IndonesiaLombokPresent, no detailsGarcía Morales et al. (2016)
IndonesiaNusa TenggaraPresent, no detailsEPPO GD (2021)
IndonesiaSulawesiPresent, no detailsEPPO GD (2021)
IndonesiaSumatraPresent, no detailsEPPO GD (2021)
IranPresent, no detailsEPPO GD (2021)
IsraelPresent, few occurrencesEPPO GD (2021)
JapanPresent, restricted distributionEPPO GD (2021)
JapanRyukyu ArchipelagoPresent, no detailsEPPO GD (2021)
JordanPresent, no detailsEPPO GD (2021)
LaosPresent, no detailsEPPO GD (2021)
LebanonPresent, no detailsEPPO GD (2021)
MalayaPresent, no detailsGarcía Morales et al. (2016)
MalaysiaPresent, no detailsEPPO GD (2021)
MalaysiaWestPresent, no detailsEPPO GD (2021)
MaldivesPresent, no detailsEPPO GD (2021)
MyanmarPresent, no detailsEPPO GD (2021)
NepalPresent, no detailsEPPO GD (2021)
OmanPresent, no detailsEPPO GD (2021)
PakistanPresent, no detailsEPPO GD (2021)
PhilippinesPresent, no detailsEPPO GD (2021)
Saudi ArabiaPresent, no detailsEPPO GD (2021)
SingaporePresent, no detailsEPPO GD (2021)
Sri LankaPresent, no detailsEPPO GD (2021)
TaiwanPresent, no detailsEPPO GD (2021)
ThailandPresent, no detailsEPPO GD (2021)
TurkeyPresent, no detailsEPPO GD (2021)
United Arab EmiratesPresent, no detailsEPPO GD (2021)
VietnamPresent, no detailsEPPO GD (2021)
YemenPresent, no detailsEPPO GD (2021)
OceaniaAustraliaPresent, no detailsEPPO GD (2021)
AustraliaNorthern TerritoryPresent, no detailsEPPO GD (2021)
AustraliaQueenslandPresent, no detailsEPPO GD (2021)
AustraliaSouth AustraliaPresent, no detailsEPPO GD (2021)
AustraliaWestern AustraliaPresent, no detailsEPPO GD (2021)
FijiPresent, no detailsEPPO GD (2021)
GuamPresent, no detailsEPPO GD (2021)
MicronesiaPresent, restricted distributionEPPO GD (2021)
New CaledoniaPresent, no detailsEPPO GD (2021)
Northern Mariana IslandsPresent, no detailsEPPO GD (2021)
PalauPresent, no detailsEPPO GD (2021)
Papua New GuineaPresent, no detailsEPPO GD (2021)
SamoaPresent, no detailsEPPO GD (2021)
Solomon IslandsPresent, no detailsEPPO GD (2021)
TongaPresent, no detailsEPPO GD (2021)
TuvaluPresent, no detailsEPPO GD (2021)
USAHawaiiPresent, no detailsEPPO GD (2021)
VanuatuPresent, no detailsEPPO GD (2021)

Table C.1: Fresh or dried citrus (CN code: 0805) imported in 100 kg into the EU (27) from regions where Maconellicoccus hirsutus is known to occur (Source: Eurostat accessed on 22/9/2021)

COUNTRY20162017201820192020
Australia3,279.841,284.38644.9710,645.402,733.47
Bangladesh227.61229.58159.67322.421,183.66
Brazil864,863.09903,432.95900,907.24822,134.46902,354.68
Burkina Faso78.14148.57103.9538.9553.52
Cameroon10.480.20
China827,840.571,084,857.271,024,163.151,108,595.221,098,691.70
Colombia44,825.3779,400.99123,887.46136,914.85172,413.40
Costa Rica4,700.31921.32704.93231.20461.60
Cuba7,165.743,863.974,438.143,422.11556.03
Dominica865.67193.3457.6576.5078.69
Egypt1,931,586.642,246,998.882,643,272.022,206,932.712,850,742.72
Guyana24.00
Haiti207.41176.5372.1031.00248.29
Hong Kong0.002.271.00
India246.801.00449.6388.51254.95
Indonesia566.73555.70779.35836.73864.54
Iran1,533.221,218.521,208.012,174.221,882.74
Jamaica3,633.973,325.11675.682,409.551,646.87
Israel799,118.49969,403.62824,601.66812,738.57878,713.15
Jordan1.170.003.791.4011.80
Japan352.58417.44270.73319.24162.50
Kenya8.8034.56
Laos51.942.1020.23
Lebanon503.211,504.917.467.283.19
Malaysia4.1839.0283.457.71
Mexico570,402.80553,818.66589,021.12443,743.54349,628.56
Nepal1,170.00
Nigeria0.030.10200.00
Pakistan2.450.59
Philippines0.207.710.10
Somalia490.30193.21367.52514.30342.10
Sudan2.1020.58
Taiwan157.490.01
Tanzania179.90190.01144.1235.9575.50
Thailand426.421,283.13659.74624.93194.87
Tunisia175,010.90172,515.76125,258.30133,950.1575,620.02
Turkey2,569,671.582,026,980.053,149,386.852,102,077.482,573,806.18
United States301,229.06231,210.47185,706.99177,755.45148,845.72
Venezuela744.082,216.36681.07
Viet Nam28,649.4646,738.1770,934.0773,964.3563,730.13

Table C.2: Cotton linters (CN code: 140420) imported in 100 kg into the EU (27) from regions where Maconellicoccus hirsutus is known to occur (Source: Eurostat accessed on 22/9/2021)

COUNTRY20162017201820192020
Benin400.00294.95608.38132.9487.99
Brazil13,493.5457,840.6368,605.7250,783.5657,176.03
China1,530.8010.0044.83102.75188.29
Egypt1.47
India1,136.10589.38487.65735.712,148.17
Indonesia27.555.38
Iran3.93
Turkey40,881.83115,022.7888,098.6682,852.5581,157.09
United States56,181.4532,472.8516,629.257,933.0619,150.08
Viet Nam0.210.34

Table C.3: Fresh or dried bananas (CN code: 0803) imported in 100 kg into the EU (27) from regions where Maconellicoccus hirsutus is known to occur (Source: Eurostat accessed on 22/9/2021)

COUNTRY20162017201820192020
Bangladesh174.6679.8572.7538.0535.64
Brazil149,108.0326,855.0859,677.31104,909.7498,434.39
Cameroon2,521,882.412,341,539.741,791,447.011,520,648.041,579,456.86
China252.64188.73390.56545.74854.93
Colombia10,120,590.1311,594,479.4611,282,545.8811,524,355.7512,193,049.39
Costa Rica9,662,138.799,663,219.6910,125,330.579,405,488.4010,342,372.80
Cuba1.28
Egypt42.980.18146.87
India515.19445.99571.13607.741,418.91
Indonesia0.0137.2714.7264.17
Iran0.092.8612.33
Israel2.100.75
Kenya1.900.726.1511.2314.95
Malaysia8.02
Mexico516,367.97558,896.47348,905.62239,173.11141,492.42
Nigeria0.722.042.500.846.35
Pakistan2.6049.70
Philippines2,480.9011,415.471,674.922,160.351,240.80
Saudi Arabia5.00
Singapore0.060.12
Taiwan0.15
Tanzania28.0211.9333.6834.2434.74
Thailand550.44674.34603.32526.15334.58
Turkey202.06210.600.14
United States7.006.371.546.3210.37
Viet Nam276.26178.84190.96210.11142.71
Zambia0.72

Table C.4: Fresh grapes (CN code: 080610) imported in 100 kg into the EU (27) from regions where Maconellicoccus hirsutus is known to occur (Source: Eurostat accessed on 22/9/2021)

COUNTRY20162017201820192020
Australia2.950.50
Bangladesh1.050.50
Brazil194,152.79249,279.81271,987.56196,465.22228,095.15
China0.006.000.03
Colombia0.00381.30669.12186.96
Egypt330,565.57404,801.23429,994.87442,798.85462,890.07
India640,933.67827,467.67722,802.04950,910.96733,881.71
Iran2,158.50366.00399.80
Israel13,169.167,165.096,397.33318.241,080.90
Japan4.841.191.171.1520.67
Kenya186.96
Mexico358.96186.71184.62
Thailand0.370.140.160.87
Tunisia657.82239.6240.60192.00
Turkey298,205.16375,776.41227,616.42272,447.02287,021.27
United States1,714.938,868.744,413.371,866.201,072.48
Zambia0.280.03

Table C.5: Fresh or dried avocados (CN code: 080440) imported in 100 kg into the EU (27) from regions where Maconellicoccus hirsutus is known to occur (Source: Eurostat accessed on 22/9/2021)

COUNTRY20162017201820192020
Brazil44,357.3671,040.5068,697.6178,673.7348,183.82
Cameroon133.50173.54221.30259.38205.93
China193.9735.281.230.04
Colombia152,115.55210,139.60251,050.33387,367.23663,149.95
Costa Rica21.569.98428.45686.40
Cuba109.0973.9441.53131.0834.33
Egypt211.205.354.5879.92363.95
India0.042.060.520.06
Israel301,123.91424,267.97370,378.23437,318.01345,663.97
Kenya228,426.16243,947.31404,593.87346,231.90435,309.11
Malaysia0.0347.04
Mexico503,687.52445,611.06463,741.28767,878.48716,205.77
Nigeria1.063.153.180.51
Tanzania26,823.0525,773.5855,517.1660,480.9650,769.74
Thailand3.689.769.669.063.39
Turkey213.41477.051,530.932,172.091,864.65
United States8,819.531.192,546.860.024.66
Viet Nam1.000.05
Zambia53.68

Table C.6: Fresh tamarinds, cashew apples, lychees, jackfruit, sapodillo plums, passion fruit, carambola and pitahaya (CN code: 08109020) imported in 100 kg into the EU (27) from regions where Maconellicoccus hirsutus is known to occur (Source: Eurostat accessed on 22/9/2021)

COUNTRY20162017201820192020
Australia12.50
Bangladesh140.15222.55291.61206.12382.00
Brazil49.36147.37368.88966.631,220.26
Cameroon41.84100.5338.5292.0046.11
China314.75287.381,112.111,014.77823.41
Colombia69,743.6372,656.3783,639.8489,847.3190,741.20
Costa Rica9.113.520.1318.62
Egypt13.7939.05
Hong Kong9.66
India324.19621.751,095.121,168.69754.33
Indonesia103.20333.37297.72246.67463.60
Iran6.251.750.503.88
Israel2,943.372,919.301,061.091,125.92594.86
Kenya714.44221.45603.11481.00697.14
Malaysia15,348.2314,205.3313,879.9214,235.967,849.69
Mexico543.90212.781,295.08669.872,331.91
Nigeria0.001.913.09
Pakistan2.223.348.17
Philippines9.7814.260.88
Singapore9.008.48
Taiwan11.9210.5925.978.97
Tanzania0.351.278.774.52
Thailand9,774.9310,279.6812,461.3814,900.2110,138.74
Turkey8.6118.9223.40
United States3.973.000.070.02
Viet Nam33,078.8238,428.6144,070.8352,846.3345,652.75
Zambia631.604,568.503,526.043,087.70

Table C.7: Fresh or dried pineapples (CN code: 08043000) imported in 100 kg into the EU (27) from regions where Maconellicoccus hirsutus is known to occur (Source: Eurostat accessed on 19/11/2021)

COUNTRY20162017201820192020
Algeria0.000.01
Aruba0.00
Australia0.000.000.01
Bahamas0.00
Belize0.00
Benin29,484.889,456.568,065.087,481.6712,849.58
Brazil1,522.021,272.34484.83639.05280.66
Burkina Faso145.9219.683.57
Cameroon38,878.7639,301.8530,633.7423,825.8313,811.36
China69.9025.059.9162.6542.74
Colombia64,893.82123,462.4591,067.0453,663.4942,136.78
Congo0.002.873.40
Congo, Democratic Republic of0.782.560.850.07
Costa Rica6,095,312.666,832,249.097,693,551.487,543,050.716,650,975.31
Côte d’Ivoire (Ivory Coast)202,205.93255,038.72220,581.56244,175.93203,552.53
Cuba10,645.214,382.573,838.501,998.42976.85
Dominican Republic29,667.0015,582.3119,723.3720,566.3520,525.91
Egypt201.6028.16
Fiji0.00
Gabon0.00
Grenada0.00
Guatemala229.7440.0864.03282.50
Guinea17.3598.3483.4572.9019.95
Guyana0.0022.00
India186.7117.9975.8511.521.00
Indonesia0.24543.770.092.50
Iran, Islamic Republic of0.000.010.00
Israel2.810.200.01
Jamaica0.00
Japan0.020.00
Jordan0.0036.00
Kenya761.13745.192,147.9723,799.06
Lao People’s Democratic Republic (Laos)0.00
Lebanon0.160.005.05
Libya0.00
Malaysia13.605.002.40
Maldives0.00
Mexico1,268.222,957.94773.74142.42174.97
Nicaragua0.00
Nigeria0.540.950.130.240.01
Oman0.00
Pakistan0.00
Palau0.00
Philippines93.71114.23183.8386.03566.04
Saudi Arabia0.000.450.17
Singapore0.200.000.29
Sri Lanka1,774.665,755.444,125.572,675.192,636.02
Suriname0.00
Taiwan0.000.070.05
Thailand10,183.3011,093.219,505.488,056.498,828.72
Trinidad and Tobago0.00
Tunisia0.050.000.010.03
Turkey0.0025.200.04
United Arab Emirates0.000.02
United States69.7256.6622.0328.2857.29
Venezuela, Bolivarian Republic of0.150.000.190.04
Viet Nam91.3165.879.8820.202.18
Virgin Islands, British0.00
Virgin Islands, United States0.00
Zambia0.00
  10 in total

1.  Hot water immersion for surface disinfestation of Maconellicoccus hirsutus (Homoptera: Pseudococcidae).

Authors:  Arnold H Hara; Christopher M Jacobsen
Journal:  J Econ Entomol       Date:  2005-04       Impact factor: 2.381

2.  Commodity risk assessment of Ficus carica plants from Israel.

Authors:  Claude Bragard; Katharina Dehnen-Schmutz; Francesco Di Serio; Marie-Agnès Jacques; Josep Anton Jaques Miret; Annemarie Fejer Justesen; Alan MacLeod; Christer Sven Magnusson; Panagiotis Milonas; Juan A Navas-Cortes; Stephen Parnell; Roel Potting; Philippe Lucien Reignault; Hans-Hermann Thulke; Wopke van der Werf; Antonio Vicent Civera; Jonathan Yuen; Lucia Zappalà; Andrea Battisti; Hugo Mas; Daniel Rigling; Olaf Mosbach-Schulz; Paolo Gonthier
Journal:  EFSA J       Date:  2021-01-21

3.  Identification of mealybug pest species (Hemiptera: Pseudococcidae) in Egypt and France, using a DNA barcoding approach.

Authors:  S Abd-Rabou; H Shalaby; J-F Germain; N Ris; P Kreiter; T Malausa
Journal:  Bull Entomol Res       Date:  2012-02-24       Impact factor: 1.750

4.  Immune response of the hibiscus mealybug, Maconellicoccus hirsutus Green (Homoptera: Pseudococcidae), to oviposition of the parasitoid Anagyrus kamali Moursi (Hymenoptera: Encyrtidae).

Authors: 
Journal:  J Insect Physiol       Date:  2000-05-01       Impact factor: 2.354

5.  Guidance on the use of the weight of evidence approach in scientific assessments.

Authors:  Anthony Hardy; Diane Benford; Thorhallur Halldorsson; Michael John Jeger; Helle Katrine Knutsen; Simon More; Hanspeter Naegeli; Hubert Noteborn; Colin Ockleford; Antonia Ricci; Guido Rychen; Josef R Schlatter; Vittorio Silano; Roland Solecki; Dominique Turck; Emilio Benfenati; Qasim Mohammad Chaudhry; Peter Craig; Geoff Frampton; Matthias Greiner; Andrew Hart; Christer Hogstrand; Claude Lambre; Robert Luttik; David Makowski; Alfonso Siani; Helene Wahlstroem; Jaime Aguilera; Jean-Lou Dorne; Antonio Fernandez Dumont; Michaela Hempen; Silvia Valtueña Martínez; Laura Martino; Camilla Smeraldi; Andrea Terron; Nikolaos Georgiadis; Maged Younes
Journal:  EFSA J       Date:  2017-08-03

6.  Guidance on quantitative pest risk assessment.

Authors:  Michael Jeger; Claude Bragard; David Caffier; Thierry Candresse; Elisavet Chatzivassiliou; Katharina Dehnen-Schmutz; Jean-Claude Grégoire; Josep Anton Jaques Miret; Alan MacLeod; Maria Navajas Navarro; Björn Niere; Stephen Parnell; Roel Potting; Trond Rafoss; Vittorio Rossi; Gregor Urek; Ariena Van Bruggen; Wopke Van Der Werf; Jonathan West; Stephan Winter; Andy Hart; Jan Schans; Gritta Schrader; Muriel Suffert; Virag Kertész; Svetla Kozelska; Maria Rosaria Mannino; Olaf Mosbach-Schulz; Marco Pautasso; Giuseppe Stancanelli; Sara Tramontini; Sybren Vos; Gianni Gilioli
Journal:  EFSA J       Date:  2018-08-03

7.  Susceptibility of Maconellicoccus hirsutus (Homoptera: Pseudococcidae) to methyl bromide.

Authors:  J Larry Zettler; Peter A Follett; Richard F Gill
Journal:  J Econ Entomol       Date:  2002-12       Impact factor: 2.381

8.  Life history of the mealybug, Maconellicoccus hirsutus (Hemiptera: Pseudococcidae), at constant temperatures.

Authors:  Juang-Horng Chong; Amy L Roda; Catharine M Mannion
Journal:  Environ Entomol       Date:  2008-04       Impact factor: 2.377

9.  ScaleNet: a literature-based model of scale insect biology and systematics.

Authors:  Mayrolin García Morales; Barbara D Denno; Douglass R Miller; Gary L Miller; Yair Ben-Dov; Nate B Hardy
Journal:  Database (Oxford)       Date:  2016-02-09       Impact factor: 3.451

10.  Laboratory Evaluation of Different Insecticides against Hibiscus Mealybug, Maconellicoccus hirsutus (Hemiptera: Pseudococcidae).

Authors:  Samman Fatima; Mubashar Hussain; Shama Shafqat; Muhammad Faheem Malik; Zaheer Abbas; Nadia Noureen; Noor Ul Ane
Journal:  Scientifica (Cairo)       Date:  2016-05-22
  10 in total

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