Abstract
The EFSA Panel on Plant Health performed a pest categorisation of Nipaecoccus viridis (Hemiptera: Sternorrhyncha: Pseudococcidae), the spherical scale, for the EU. It is of Asian origin and occurs widely in southern Asia, Africa and tropical Australia. It has been introduced to a few countries in the Americas. In the Mediterranean basin it is found in Algeria, Egypt, Israel, Syria and Turkey, where it is limited to the Marmara region. It has not been reported within the EU. It is not listed in Annex II of Commission Implementing Regulation (EU) 2019/2072. It reproduces sexually, has three generations each year in citrus orchards in South Africa, and all stages can overwinter. First instar nymphs may move to neighbouring plants by crawling or be passively dispersed by wind or hitchhiking on clothing, equipment or animals. It is highly polyphagous, feeding on plants in 115 genera and 46 families. It is an important pest of citrus (Citrus spp.), cotton (Gossypium spp.), mango (Mangifera indica), avocado (Persea americana) and stored potatoes (Solanum tuberosum). It also feeds on a wide range of other fruit (apple Malus domestica, olive Olea europea, pear Pyrus communis and grape Vitis vinifera) and vegetable crops (tomato Solanum lycopersicum), and ornamental plants (roses, Rosa spp.) that are widely grown in the EU. Plants for planting, fruits, vegetables, and cut flowers are the main potential pathways for entry of N. viridis into the EU. Climatic conditions and availability of host plants in southern parts of the EU where there are few days of frost each year would likely allow this species to successfully establish and spread. Reductions in yield and quality of cultivated hosts including avocado, citrus, cotton and mango is anticipated if establishment occurs. Phytosanitary measures are available to reduce the likelihood of entry and spread. N. viridis meets the criteria that are within the remit of EFSA to assess for this species to be regarded as a potential Union quarantine pest.
Keywords: spherical mealybug, invasive species, pest risk, plant health, plant pest, quarantine
1. Introduction
1.1. Background and Terms of Reference as provided by the requestor
1.1.1. 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.
1.1.2. 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.
1.2. Interpretation of the Terms of Reference
Nipaecoccus viridis is one of a number of pests listed in Annex 1D to the Terms of Reference (ToR) to be subject to pest categorisation to determine whether it fulfils the criteria of a potential Union quarantine pest (QP) 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 EU 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 QP, risk reduction options will be identified.
1.3. Additional information
This pest categorisation was initiated as a result of media monitoring, PeMoScoring and subsequent discussion in PAFF, resulting in it being included in the current mandate within the list of pests identified by horizon scanning and selected for pest categorisation.
2. Data and methodologies
2.1. Data
2.1.1. Literature search
A literature search on N. viridis 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.
2.1.2. 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 2.1.1.
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 European Union, 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.
GenBank was searched to determine whether it contained any nucleotide sequences for N. viridis which could be used as reference material for molecular diagnosis. GenBank® (www.ncbi.nlm.nih.gov/genbank/) is a comprehensive publicly available database that as of August 2019 (release version 227) contained over 6.25 trillion base pairs from over 1.6 billion nucleotide sequences for 450,000 formally described species (Sayers et al., 2020).
2.2. Methodologies
The Panel performed the pest categorisation for N. viridis, 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 QP is given in Regulation (EU) 2016/2031 Article 3 and Annex I, Section 1 of the 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 derived from 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 clearly defined, 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 in a limited part of the EU or is it scarce, irregular, isolated or present infrequently? If so, the pest is considered to be not widely distributed. |
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 for entry and spread. |
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 pest entry, establishment, spread or impacts? |
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. |
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.
3. Pest categorisation
3.1. Identity and biology of the pest
3.1.1. Identity and taxonomy
Is the identity of the pest clearly defined, or has it been shown to produce consistent symptoms and/or to be transmissible?
Yes, the identity of the species is established and N. viridis (Newstead) is the accepted name.
N. viridis (Newstead, 1894) is an insect in the order Hemiptera, suborder Sternorrhyncha, and family Pseudococcidae. It has many common names including coffee mealybug, cotton mealybug, hibiscus mealybug, globular coffee mealybug, karoo thorn mealybug, Lebbeck mealybug and spherical mealybug. However, the common name cotton mealybug is more commonly applied to Phenacoccus solenopsis Tinsley (EFSA PLH Panel, 2021) while hibiscus mealybug can be confused with pink hibiscus mealybug Maconellicoccus hirsutus (Green), as the mealybugs share many host plants (EFSA PLH Panel, 2022).
It was first described as Dactylopius viridis by Newstead (1894) from specimens collected in Madras, India, on Hygrophila auriculata (= Hygrophila spinosa). The main synonyms are: Dactylopius perniciosus Newstead & Willcocks; Dactylopius vastator Maskell; Nipaecoccus vastator (Maskell); Pseudococcus filamentosus corymbatus Green; Pseudococcus perniciosus Newstead; Pseudococcus solitarius Brain; Pseudococcus theae (Rutherford); Pseudococcus vastator (Maskell); Pseudococcus viridis (Newstead); Ripersia theae Rutherford; and Trionymus sericeus James. A comprehensive synonymy is provided by García Morales et al. (2016).
The EPPO code1 (Griessinger and Roy, 2015; EPPO, 2019) for this species is: NIPAVI (EPPO, online).
3.1.2. Biology of the pest
The biology of N. viridis was reviewed by Sharaf and Meyerdirk (1987). It reproduces sexually and each female lays 90–138 eggs. There are three immature instars in the female and four in the male and all stages can overwinter. Three generations per year are recorded in citrus orchards in South Africa (Cilliers and Bedford, 1978). The spring (September–October) generation of mature females lays eggs that hatch during October‐November. The crawlers migrate and settle mainly in protected areas, under the sepals of the fruitlets when the fruit are pea‐sized or larger. This second generation matures in November and lays eggs which hatch during December. The third generation of females matures in late summer‐early autumn (March‐April). In laboratory studies, N. viridis females can develop from egg to reproductive adult on citrus trees in approximately 19 days and the male can develop in 15 days at 32.5°C and 72.1% RH (Sharaf and Meyerdirk, 1987). There were significant positive correlations between population density and temperature, and negative correlations with relative humidity (Kondo and Watson, 2022).
More than 84 species of predators (mainly Coccinellidae) and parasitoids (mainly Encyrtidae) have been recorded for N. viridis (García Morales et al., 2016; Sharaf and Meyerdirk, 1987). Several of the predators and parasitoids of N. viridis are already present in the EU. The parasitoid Anagyrus agraensis Saraswat (Hymenoptera: Encyrtidae) has been successfully used for the biocontrol of the pest in Jordan and Israel. The wasp is not present in the EU but if the mealybug spreads to the EU, the parasitoid is likely to follow, or could be deliberately introduced. The ant species that attend and protect the mealybugs from natural enemies are discussed by Kondo and Watson (2022).
3.1.3. Host range/Species affected
N. viridis is highly polyphagous and has been recorded on hosts in 115 genera belonging to 46 plant families (García Morales et al., 2016; Kondo and Watson, 2022). Appendix A provides the full list of plant species reported to be hosts for N. viridis. Economically important crops in the EU include celery (Apium graveolens), asparagus (Asparagus officinalis), papaya (Carica papaya), citrus (Citrus spp.), common fig (Ficus carica), soybean (Glycine max), cotton (Gossypium spp.), sunflower (Helianthus annuus), apple (Malus domestica), mango (Mangifera indica), white mulberry (Morus alba), black mulberry (Morus nigra), olive (Olea europea), avocado (Persea americana), apricot (Prunus armeniaca), guava (Psidium guajava), pomegranate (Punica granatum), pear (Pyrus communis), tomato (Solanum lycopersicon), potato (Solanum tuberosum) and grape (Vitis vinifera). However, there is uncertainty regarding the impact of N. viridis on many of these hosts (see Section 3.5). Hosts also include ornamental plants found in the EU including chrysanthemums (Chrysanthemum spp.), hibiscus (Hibiscus spp.), myrtle (Mrytus communis), oleander (Nerium oleander), geranium (Pelargonium spp.) and roses (Rosa spp.).
3.1.4. Intraspecific diversity
No intraspecific diversity is reported for this species.
3.1.5. 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 N. viridis.
Detection
Careful visual examination of plants is an effective way for the detection of the insect. The white waxy covering of the mealybugs and the waxy ovisacs allow detection (Figure 1). They are often gregarious, and clusters of the mealybugs can be conspicuous on above‐ground new growth and fruit. The adult waxy secretions may appear to form a continuous layer over the cluster making it difficult to discern individual mealybugs (Kondo and Watson, 2022). In contrast, they may also hide in cracks and crevices on the plant bark and under the sepals of fruits, making detection of early infestations difficult.
Figure 1.
Nipaecoccus viridis: (A) adult females and ovisacs hidden in the crevices on Annona squamosa fruit; (B) adult female, dorsal view, on Citrus macroptera fruit; (C) adult female with ovisac developing on the left and lifting the female body off the surface of the fruit by almost 90 degrees; (D) ovisac opened to reveal the dark purple eggs. Adult female body length about 4 mm (source: Chris Malumphy)
N. viridis can be confused with other scale insects in the field. For example, it was confused with cottony cushion scale Icerya purchasi Maskell (Hemiptera: Sternorrhyncha: Monophlebidae) in commercial citrus orchards in Florida (Diepenbrock and Ahmed, 2020), it should be noted that I. purchasi is common in the EU.
Symptoms
The main symptoms of N. viridis infestation are:
General weakening of the host due to sap removal.
Defoliation, dieback and mortality of young plants.
Citrus foliage and fruit can be severely distorted.
Plants become covered in sooty moulds that grow on the honeydew egested by the mealybugs.
Plants may also become contaminated with wax, particularly from the sticky ovisac wax.
With the exception of the white wax contamination and distortion of citrus fruit and foliage, these symptoms are similar to those caused by many other phloem‐feeding insects and should not be considered as diagnostic
Identification
The identification of N. viridis requires microscopic examination of slide‐mounted adult females and verification of the presence of key morphological characteristics as given in Ghosh and Ghose (1989), Williams (1985, 2004), and Kondo and Watson (2022). Joshi et al. (2021) provide photographs and keys for the identification of live and slide‐mounted adult females of 10 species of mealybug infesting cassava in India. This includes N. viridis and several other polyphagous, widespread species that share many of the same host species. The adult male and immature stages of N. viridis have been described by Ghosh and Ghose (1989). Molecular techniques based on cytochrome‐oxidase 1 (COI) have also been developed by Gaines et al. (2022) for species identification.
Description
The main morphological characters are:
Adult female oval and flattish initially, becoming globular with maturity, up to 4 mm long and 3 mm wide; body contents black to dark purple; body covered with thick white wax (Figure 1B) which may become pale‐yellow over time.
The ovisac of sticky white wax forms under the abdomen; when full of eggs, it lifts the abdomen of the adult female up to a steep angle, often almost 90 degrees, to the plant surface (Figure 1C).
Eggs (Figure 1D) and first‐instar nymphs are purple.
The protective wax cover for male prepupa and pupa occurs on the foliage; it is parallel sided, formed from white wax filaments, and about 2 mm long.
3.2. Pest distribution
3.2.1. Pest distribution outside the EU
N. viridis is mainly a tropical species of Asian origin. It is widespread in southern Asia, Africa and tropical Australia; it has been introduced to a few countries in the Americas (Figure 2). N. viridis was first recorded in Egypt a century ago (Hall, 1923), yet it only spread to neighbouring Israel in the 1980s (Ben‐Dov et al., 1985), and was recently found in Turkey (Ülgentürk et al., 2022). In the Mediterranean basin, it is also present in Algeria and Syria. For a detailed list of countries where N. viridis is present, see Appendix B.
Figure 2.
Global distribution of Nipaecoccus viridis (Source: EPPO Global Database accessed on 04/11/22)
3.2.2. Pest distribution in the EU
Is the pest present in the EU territory? If present, is the pest in a limited part of the EU or is it scarce, irregular, isolated or present infrequently? If so, the pest is considered to be not widely distributed.
No, N. viridis is not known to be present in the EU.
3.3. Regulatory status
3.3.1. Commission Implementing Regulation 2019/2072
N. viridis is not listed in Annex II of Commission Implementing Regulation (EU) 2019/2072, an implementing act of Regulation (EU) 2016/2031, or in any emergency plant health legislation.
3.3.2. 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 N. viridis hosts in the Union from certain third countries is prohibited (Table 2).
Table 2.
List of plants, plant products and other objects that are Nipaecoccus viridis 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 | |||
---|---|---|---|
Description | CN Code | Third country, group of third countries or specific area of third country | |
1. | Plants of […]., Pinus L., […]., other than fruit and seeds |
ex 0602 20 20 ex 0602 20 80 ex 0602 90 41 ex 0602 90 45 ex 0602 90 46 ex 0602 90 47 ex 0602 90 50 ex 0602 90 70 ex 0602 90 99 ex 0604 20 20 ex 0604 20 40 |
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, Ukraine and the United Kingdom |
8. | Plants for planting of […]., 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, Ukraine and the United Kingdom |
9. | Plants for planting of Cydonia Mill., Malus Mill., Prunus L. and Pyrus L. and their hybrids, and […], 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, the United Kingdom (1) and United States other than Hawai |
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., […]., and their hybrids, other than fruits and seeds |
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 |
All third countries |
15 | Tubers of Solanum tuberosum L., seed potatoes* | 0701 10 00 | Third countries other than Switzerland |
16. | Plants for planting of stolon‐ or tuber‐forming species of Solanum L. or their hybrids, other than those tubers of Solanum tuberosum L. as specified in entry 15 |
ex 0601 10 90 ex 0601 20 90 ex 0602 90 50 ex 0602 90 70 ex 0602 90 91 ex 0602 90 99 |
Third countries other than Switzerland |
17. | Tubers of species of Solanum L., and their hybrids, other than those specified in entries 15 and 16 |
ex 0601 10 90 ex 0601 20 90 0701 90 10 0701 90 50 0701 90 90 |
Third countries or regions other than: (a) Algeria, Egypt, Israel, Libya, Morocco, Syria, Switzerland, Tunisia and Turkey; or (b) those which fulfil the following: (i) they are one of following: Albania, Andorra, Armenia, Azerbaijan, Belarus, Canary Islands, Faeroe Islands, Georgia, Iceland, Liechtenstein, Moldova, Monaco, 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 and Ukraine; and (ii) they fulfil one of the following: — they are recognised as being free from Clavibacter sepedonicus (Spieckermann and Kotthoff) Nouioui et al., in accordance with the procedure referred to in Article 107 of Regulation (EU) 2016/2031, or their legislation is recognised as equivalent to the Union rules concerning protection against Clavibacter sepedonicus (Spieckermann and Kotthoff) Nouioui et al. in accordance with the procedure referred to in Article 107 of Regulation (EU) 2016/2031; or (c) Bosnia and Herzegovina, Montenegro, Serbia and the United Kingdom (1), provided the following condition is fulfilled: the submission by those third countries to the Commission, by 30 April of each year, of survey results of the previous year confirming that Clavibacter sepedonicus (Spieckermann and Kotthoff) Nouioui et al. is not present on their territories |
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 ex 0602 10 90 |
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, Ukraine and the United Kingdom |
: N. viridis is a pest of stored potato tubers in Asia but is very unlikely to be found on seed potatoes.
Plants for planting of Acacia Mill., Albizia Durazz., Annona L., Caesalpinia L., Diospyros L., Ficus L., Ligustrum L., Malus Mill., Persea Mill., Prunus L. and Robinia L., which are hosts of N. viridis (Appendix A) are considered High Risk Plants for the EU and their import is prohibited pending country‐specific commodity risk assessment (EU 2018/2019).
3.4. Entry, establishment and spread in the EU
3.4.1. Entry
Is the pest able to enter into the EU territory? If yes, identify and list the pathways.
Yes, pathways for entry into the EU territory exist via plants for planting, fruit, cut flowers, and vegetables, although some host plants for planting are prohibited, closing some potential pathways (Table 3).
Comment on plants for planting as a pathway.
Plants for planting (excluding seeds) would be the primary pathway for entry (Table 3).
Table 3.
Potential pathways for Nipaecoccus viridis into the EU
Pathways (e.g. host/intended use/source) | Life stage | Relevant mitigations [e.g. prohibitions (Annex VI), special requirements (Annex VII) or phytosanitary certificates (Annex XI) within Implementing Regulation 2019/2072] |
---|---|---|
Plants for planting | Eggs, nymphs, adult females | The import of some host plants of N. viridis for planting from all or certain 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. |
Fresh fruits and vegetables, and cut flowers | Eggs, nymphs, adult females | A phytosanitary certificate is required to import fresh fruits and vegetables, and cut flowers into the EU (2019/2072, Annex XI, Part A and B) unless exempt by being listed in 2019/2072 Annex XI, Part C. |
N. viridis can spread over long distances through plants for planting, fruit, cut flowers, and vegetables (Table 3).
No specific requirements are set for N. viridis. As not all, but only a proportion of imported consignments are liable to be physically inspected, the requirements summarised in Table 3 do not preclude the entry of N. viridis.
Annual imports of N. viridis hosts from countries where the pest is known to occur are provided in Appendix C with total imports shown in Table 4 below (Table C.1, C.2, C.3, C.4, C.5, C.6, C.7, C.8, C.9, C.10, C.11, C.12, C.13, C.14, C.15, C.16, C.17, C.18, C.19, C.20–C.21).
Table 4.
EU imports of Nipaecoccus viridis hosts 2016–2020 (Source: EUROSTAT; in hundreds of kg)
Crops | 2016 | 2017 | 2018 | 2019 | 2020 |
---|---|---|---|---|---|
Soya beans, whether or not broken | 53,494,472 | 47,824,702 | 74,966,338 | 68,291,705 | 49,452,878 |
Coffee, whether or not roasted or decaffeinated; coffee husks and skins; coffee substitutes containing coffee in any proportion | 12,482,224 | 12,148,510 | 12,624,998 | 12,249,202 | 11,824,107 |
Potatoes, fresh or chilled | 2,860,992 | 3,434,079 | 3,003,074 | 4,199,875 | 3,542,514 |
Grapes, fresh or dried | 3,098,466 | 3,329,071 | 3,245,073 | 3,584,443 | 3,517,427 |
Fresh or dried grapefruit | 2,321,979 | 2,493,519 | 2,473,050 | 2,432,975 | 2,365,773 |
Coconuts, Brazil nuts and cashew nuts, fresh or dried, whether or not shelled or peeled | 2,006,480 | 2,145,538 | 2,138,013 | 2,238,882 | 2,355,408 |
Fresh or dried avocados | 1,504,157 | 1,478,278 | 1,989,007 | 2,049,056 | 2,007,256 |
Fresh or dried lemons “Citrus limon, Citrus limonum” | 477,586 | 594,392 | 862,762 | 969,365 | 1,507,425 |
Fresh or dried guavas, mangoes and mangosteens | 770,133 | 770,026 | 819,623 | 893,079 | 758,329 |
Fresh pears | 968,156 | 858,536 | 774,153 | 674,488 | 683,078 |
Fresh or dried dates | 444,823 | 545,344 | 566,712 | 586,247 | 686,948 |
Fresh or dried limes “Citrus aurantifolia, Citrus latifolia” | 441,370 | 462,663 | 567,649 | 410,027 | 340,818 |
Fresh apples | 319,435 | 263,465 | 369,165 | 269,200 | 341,461 |
Fresh tamarinds, cashew apples, lychees, jackfruit, sapodillo plums, passion fruit, carambola and pitahaya | 285,469 | 275,602 | 284,775 | 290,278 | 236,695 |
Tomatoes, fresh or chilled | 118,141 | 87,567 | 107,723 | 98,011 | 84,342 |
Fresh or chilled asparagus | 40,277 | 42,947 | 42,064 | 47,221 | 40,110 |
Fresh, chilled, frozen or dried roots and tubers of manioc “cassava”, whether or not sliced or in the form of pellets | 16,187 | 13,681 | 24,580 | 53,683 | 75,959 |
Fresh or chilled aubergines “eggplants” | 15,883 | 18,917 | 21,105 | 22,041 | 23,669 |
Fresh pawpaws “papayas” | 11,795 | 13,495 | 14,432 | 14,757 | 11,473 |
Cucumbers and gherkins, fresh or chilled | 11,257 | 14,260 | 15,059 | 12,859 | 8,586 |
Fresh persimmons | 3,245 | 4,049 | 1,371 | 8,040 | 8,226 |
Fresh figs | 3,058 | 2,283 | 2,226 | 1,608 | 1,248 |
Fresh or chilled celery (excl. celeriac) | 183 | 571 | 336 | 505 | 467 |
Fresh quinces | 192 | 420 | 2 | 19 | 766 |
Fresh or chilled olives (excl. for oil production) | 73 | 19 | 33 | 91 | 141 |
Table C.1.
Fresh or chilled celery (excl. celeriac) (CN code: 0709 40 00) imported in 100 kg into the EU (27) from regions where Nipaecoccus viridis is known to occur (Source: Eurostat accessed on 30/4/2022)
Country | 2016 | 2017 | 2018 | 2019 | 2020 |
---|---|---|---|---|---|
Mexico | : | : | 0.02 | 0.04 | : |
Laos | 41.09 | 49.31 | 6.22 | 29.41 | 29.01 |
Egypt | : | : | 2.15 | 100.00 | 362.88 |
Kenya | 0.43 | : | : | : | : |
Uganda | 0.03 | : | : | : | : |
Togo | 5.00 | : | : | : | : |
Cambodia | : | : | : | 0.10 | : |
Jordan | : | : | : | 2.31 | : |
Israel | 13.53 | 384.31 | 210.98 | 285.19 | 10.08 |
Iran | : | 3.00 | : | : | : |
Indonesia | : | : | 0.02 | : | : |
Malaysia | : | 0.21 | : | 2.11 | 2.62 |
Sri Lanka | 0.02 | 2.52 | 0.19 | : | : |
Thailand | 122.09 | 129.77 | 110.24 | 86.17 | 62.54 |
Pakistan | : | : | : | 0.02 | : |
Viet Nam | 0.64 | 2.34 | 6.19 | : | 0.01 |
Total | 182.83 | 571.46 | 336.01 | 505.35 | 467.14 |
Table C.2.
Fresh tamarinds, cashew apples, lychees, jackfruit, sapodillo plums, passion fruit, carambola and pitahaya (CN code: 0810 90 20) imported in 100 kg into the EU (27) from regions where Nipaecoccus viridis is known to occur (Source: Eurostat accessed on 30/4/2022)
Country | 2016 | 2017 | 2018 | 2019 | 2020 |
---|---|---|---|---|---|
United States | 3.97 | 3.00 | 0.07 | : | 0.02 |
Mexico | 543.90 | 212.78 | 1295.08 | 669.87 | 2331.91 |
Angola | 0.20 | : | 98.60 | 205.72 | 435.93 |
Laos | 1269.84 | 847.10 | 542.10 | 469.73 | 238.57 |
China | 314.75 | 287.38 | 1112.11 | 1014.77 | 823.41 |
Benin | : | 0.80 | |||
Burkina Faso | : | 5.40 | : | 5.23 | 3.50 |
Côte d'Ivoire | : | 1.29 | 19.76 | 7.90 | 10.19 |
Egypt | : | 13.79 | : | : | 39.05 |
Kenya | 714.44 | 221.45 | 603.11 | 481.00 | 697.14 |
Madagascar | 173510.13 | 155018.24 | 164639.51 | 164524.38 | 135809.60 |
Mauritius | 2707.68 | 787.16 | 2685.52 | 1167.15 | 1145.97 |
Mali | : | : | 24.40 | 6.44 | 25.28 |
Nigeria | : | : | : | 1.91 | 3.09 |
South Africa | 39656.26 | 45282.45 | 30643.15 | 27215.68 | 19903.15 |
Zambia | 631.60 | 4568.50 | 3526.04 | 3087.69 | |
Rwanda | 0.18 | 4.77 | 0.22 | 11.75 | 17.28 |
Uganda | 500.68 | 682.07 | 698.61 | 666.57 | 571.89 |
Senegal | 174.50 | 9.14 | 15.30 | ||
Togo | 7.44 | 2.66 | 3.86 | 6.36 | 12.44 |
Tanzania | 0.35 | 1.27 | 8.77 | 4.52 | |
Zimbabwe | 3880.59 | 3622.61 | 3725.92 | 4324.34 | 4886.79 |
Bangladesh | 140.15 | 222.55 | 291.61 | 206.12 | 382.00 |
Myanmar | : | : | : | : | 9.96 |
Cambodia | 84.38 | 546.37 | 806.76 | 1101.17 | 712.82 |
Japan | 0.07 | 0.02 | |||
India | 324.19 | 621.75 | 1095.12 | 1168.69 | 754.33 |
Israel | 2943.37 | 2919.30 | 1061.09 | 1125.92 | 594.86 |
Iran | 6.25 | : | 1.75 | 0.50 | 3.88 |
Indonesia | 103.20 | 333.37 | 297.72 | 246.67 | 441.64 |
Malaysia | 15348.23 | 14205.33 | 13879.92 | 14235.96 | 7849.58 |
Saudi Arabia | |||||
Sri Lanka | 347.84 | 392.81 | 104.84 | 104.62 | 85.24 |
Australia | : | : | : | : | 12.50 |
Singapore | 9.00 | : | 8.48 | : | : |
Philippines | 9.78 | 14.26 | : | 0.88 | : |
Thailand | 9774.93 | 10279.68 | 12461.38 | 14900.21 | 10138.75 |
Taiwan | 11.92 | : | 10.59 | 25.97 | 8.97 |
Pakistan | 2.22 | 3.34 | 8.17 | : | : |
Syria | 0.17 | 2.00 | : | : | : |
Viet Nam | 33078.82 | 38428.61 | 44070.83 | 52846.33 | 45652.67 |
Total | 285469.36 | 275602.26 | 284775.42 | 290277.47 | 236694.62 |
Table C.3.
Fresh tamarinds, cashew apples, lychees, jackfruit, sapodillo plums, passion fruit, carambola and pitahaya (CN code: 0810 90 20) imported in 100 kg into the EU (27) from regions where Nipaecoccus viridis is known to occur (Source: Eurostat accessed on 30/4/2022)
Country | 2016 | 2017 | 2018 | 2019 | 2020 |
---|---|---|---|---|---|
United States | 396.10 | 487.57 | 757.90 | 290.34 | 242.32 |
Mexico | 37911.10 | 40833.08 | 39774.49 | 44987.19 | 37198.92 |
Laos | 0.02 | : | : | : | 0.48 |
China | : | 0.04 | : | 11.28 | 1575.35 |
Côte d'Ivoire | : | : | 12.68 | : | : |
Egypt | 0.06 | : | 2.96 | 7.32 | : |
Eritrea | : | : | : | : | : |
Kenya | 34.21 | 19.98 | 12.03 | 71.08 | 17.85 |
Madagascar | 0.13 | 1.20 | 75.57 | 330.52 | 62.13 |
Cambodia | : | : | : | 0.06 | 0.01 |
Japan | 0.02 | 0.11 | 0.07 | : | : |
India | : | : | 0.01 | : | : |
Israel | : | : | 0.17 | 0.15 | |
Malaysia | : | : | : | 0.94 | 2.13 |
Sri Lanka | : | : | : | 0.10 | : |
Australia | 10.00 | : | : | : | : |
Singapore | : | : | : | : | 0.02 |
Thailand | 1855.02 | 1584.69 | 1407.76 | 1519.97 | 874.24 |
Taiwan | : | : | : | 2.24 | : |
Syria | : | : | 19.52 | : | : |
Viet Nam | 0.01 | : | : | : | 0.04 |
Total | 40276.59 | 42946.74 | 42063.76 | 47221.40 | 40109.92 |
Table C.4.
Fresh or chilled asparagus (CN code: 0709 20 00) imported in 100 kg into the EU (27) from regions where Nipaecoccus viridis is known to occur (Source: Eurostat accessed on 30/4/2022)
Country | 2016 | 2017 | 2018 | 2019 | 2020 |
---|---|---|---|---|---|
United States | 396.10 | 487.57 | 757.90 | 290.34 | 242.32 |
Mexico | 37911.10 | 40833.08 | 39774.49 | 44987.19 | 37198.92 |
Laos | 0.02 | : | : | : | 0.48 |
China | : | 0.04 | : | 11.28 | 1575.35 |
Côte d'Ivoire | : | : | 12.68 | : | |
Egypt | 0.06 | : | 2.96 | 7.32 | : |
Kenya | 34.21 | 19.98 | 12.03 | 71.08 | 17.85 |
Madagascar | 0.13 | 1.20 | 75.57 | 330.52 | 62.13 |
South Africa | 69.92 | 20.06 | 0.60 | 0.21 | 136.43 |
Cambodia | : | : | : | 0.06 | 0.01 |
Japan | 0.02 | 0.11 | 0.07 | : | : |
India | : | : | 0.01 | : | : |
Israel | : | 0.01 | 0.17 | 0.15 | : |
Malaysia | : | : | : | 0.94 | 2.13 |
Sri Lanka | : | : | : | 0.10 | : |
Australia | 10.00 | : | : | : | : |
Singapore | : | : | : | : | 0.02 |
Thailand | 1855.02 | 1584.69 | 1407.76 | 1519.97 | 874.24 |
Taiwan | : | : | : | 2.24 | : |
Syria | : | : | 19.52 | : | : |
Viet Nam | 0.01 | : | : | : | 0.04 |
Total | 40276.59 | 42946.74 | 42063.76 | 47221.40 | 40109.92 |
Table C.5.
Fresh pawpaws “papayas” (CN code: 0807 20 00) imported in 100 kg into the EU (27) from regions where Nipaecoccus viridis is known to occur (Source: Eurostat accessed on 30/4/2022)
Country | 2016 | 2017 | 2018 | 2019 | 2020 |
---|---|---|---|---|---|
United States | 200.21 | 84.83 | 118.34 | 19.80 | 42.16 |
Mexico | 456.27 | 2793.18 | 2613.06 | 2918.40 | 2191.29 |
Angola | 302.53 | 777.89 | 2795.00 | ||
Laos | 449.13 | 296.22 | 364.27 | 527.13 | 469.50 |
China | : | : | : | 3.00 | : |
Benin | : | 5.15 | 0.80 | 1.39 | 0.98 |
Burkina Faso | : | 9.60 | 14.11 | 7.60 | : |
Côte d'Ivoire | 540.78 | 23.03 | 5.17 | : | 6.22 |
Egypt | : | 48.00 | : | : | |
Kenya | 0.48 | : | : | 1.50 | 48.35 |
Madagascar | : | 8.82 | 10.64 | : | |
Mauritius | 16.63 | : | : | : | : |
Nigeria | 0.18 | : | : | : | : |
South Africa | 2.20 | 123.55 | 377.24 | 478.96 | 14.08 |
Uganda | 9.53 | 56.11 | 17.22 | 25.61 | 23.97 |
Senegal | 24.73 | 0.94 | : | : | : |
Togo | 269.51 | 125.33 | 121.15 | 114.23 | 104.81 |
Tanzania | 0.78 | 0.56 | : | : | |
Bangladesh | 379.81 | 147.75 | 138.57 | 62.33 | 21.95 |
Cambodia | 397.26 | 514.79 | 513.79 | 338.37 | 375.98 |
India | 266.16 | 336.28 | 378.24 | 564.48 | 130.39 |
Israel | 666.65 | 661.56 | 714.92 | 276.69 | 224.50 |
Indonesia | 0.08 | 0.18 | 0.04 | 62.58 | 42.72 |
Malaysia | 53.69 | 114.20 | 12.85 | 38.99 | 0.27 |
Sri Lanka | 841.21 | 656.39 | 449.05 | 540.82 | 92.27 |
Philippines | : | 3.96 | 1.21 | 1.26 | : |
Thailand | 6494.24 | 7334.28 | 7831.20 | 7562.99 | 4561.88 |
Taiwan | : | 0.00 | : | 1.99 | : |
Pakistan | : | 5.60 | 19.01 | 5.37 | : |
Viet Nam | 726.15 | 200.97 | 381.47 | 413.60 | 327.07 |
New Caledonia | : | : | : | 1.00 | : |
Total | 11794.90 | 13494.68 | 14431.62 | 14756.62 | 11473.39 |
Table C.6.
Fresh or dried lemons (Citrus limon, Citrus limonum) and limes (Citrus aurantifolia, Citrus latifolia) (CN code: 0805 50) imported in 100 kg into the EU (27) from regions where Nipaecoccus viridis is known to occur (Source: Eurostat accessed on 30/4/2022)
Country | 2016 | 2017 | 2018 | 2019 | 2020 |
---|---|---|---|---|---|
United States | 2235.14 | 237.15 | 421.30 | 428.24 | 5872.01 |
Mexico | 414964.64 | 419216.51 | 506848.43 | 350914.58 | 285487.23 |
Angola | 0.00 | 0.00 | 42.53 | 0.00 | 0.00 |
Laos | 50.81 | 0.00 | 0.00 | 0.00 | 11.53 |
China | 260.72 | 2.10 | 1.02 | 44.48 | 6397.15 |
Burkina Faso | 59.15 | 139.20 | 103.95 | 34.25 | 51.92 |
Côte d'Ivoire | 0.00 | 0.00 | 246.40 | 0.00 | 0.00 |
Egypt | 14242.68 | 30762.76 | 28809.28 | 22439.74 | 45339.11 |
Kenya | 0.00 | 0.00 | 0.00 | 0.00 | 34.56 |
Madagascar | 0.10 | 0.00 | 5.60 | 0.04 | 13.98 |
Mauritius | 0.00 | 0.00 | 14.00 | 0.00 | 7.35 |
South Africa | 443077.77 | 561932.38 | 819786.01 | 944806.26 | 1448946.40 |
Uganda | 1.38 | 2.14 | 4.42 | 7.35 | 9.77 |
Senegal | 0.00 | 0.20 | 0.00 | 0.00 | 0.00 |
Togo | 0.00 | 0.00 | 6.24 | 0.42 | 0.00 |
Sudan | 0.00 | 0.00 | 2.10 | 0.00 | 20.08 |
Tanzania | 0.00 | 0.00 | 0.20 | 0.00 | 0.00 |
Zimbabwe | 0.00 | 0.00 | 0.00 | 243.69 | 1019.19 |
Bangladesh | 200.74 | 42.32 | 73.75 | 249.07 | 759.70 |
Afghanistan | 0.01 | 0.00 | 0.00 | 2.00 | 0.00 |
Cambodia | 0.00 | 0.01 | 0.00 | 0.00 | 0.25 |
Japan | 161.04 | 256.25 | 114.53 | 215.60 | 67.19 |
Jordan | 1.16 | 0.00 | 3.79 | 1.40 | 11.81 |
Iraq | 0.00 | 3.60 | 6.30 | 0.00 | 20.00 |
India | 79.92 | 1.00 | 33.75 | 17.16 | 0.50 |
Israel | 17010.88 | 2675.62 | 15817.68 | 1982.47 | 416.24 |
Iran | 943.28 | 667.21 | 863.69 | 822.42 | 1173.30 |
Indonesia | 166.21 | 82.06 | 315.30 | 248.39 | 142.13 |
Malaysia | 4.18 | 5.54 | 2.46 | 0.81 | 0.00 |
Sri Lanka | 0.00 | 80.95 | 95.62 | 0.20 | 12.80 |
Australia | 243.68 | 100.78 | 332.74 | 547.62 | 5.75 |
Philippines | 0.00 | 0.00 | 0.20 | 2.29 | 0.00 |
Thailand | 13.85 | 23.19 | 72.00 | 14.00 | 15.10 |
Pakistan | 0.00 | 0.00 | 2.25 | 0.59 | 0.00 |
Syria | 0.81 | 31.06 | 0.00 | 4.30 | 6.47 |
Viet Nam | 25237.78 | 40793.00 | 56385.62 | 56364.39 | 52401.63 |
Total | 918955.93 | 1057055.03 | 1430411.19 | 1379391.76 | 1848243.15 |
Table C.7.
Fresh or dried grapefruit (CN code: 0805 40 00) imported in 100 kg into the EU (27) from regions where Nipaecoccus viridis is known to occur (Source: Eurostat accessed on 30/4/2022)
Country | 2016 | 2017 | 2018 | 2019 | 2020 |
---|---|---|---|---|---|
United States | 259620.77 | 194063.68 | 130312.27 | 134522.83 | 101349.91 |
Mexico | 132997.10 | 128233.11 | 77846.41 | 89037.20 | 55247.60 |
China | 827310.17 | 1084839.19 | 1023348.37 | 1108528.93 | 1092246.65 |
Côte d'Ivoire | 224.00 | ||||
Egypt | 2701.17 | 1580.15 | 3261.41 | 4411.51 | 3048.70 |
South Africa | 818033.13 | 851594.34 | 978681.31 | 921280.18 | 854916.87 |
Uganda | : | : | : | : | 2.11 |
Sudan | : | : | : | : | 0.50 |
Tanzania | 9.90 | : | 3.40 | 9.78 | : |
Zimbabwe | 19385.06 | 16919.26 | 25612.29 | 15209.77 | 16496.04 |
Bangladesh | : | 171.60 | : | : | : |
India | 5.00 | : | : | 7.89 | |
Israel | 257904.61 | 208679.65 | 218945.84 | 141834.58 | 230981.55 |
Iran | : | : | 56.60 | : | 19.45 |
Indonesia | : | : | 0.03 | : | : |
Malaysia | : | : | 7.82 | : | : |
Thailand | 376.42 | 1224.53 | 484.17 | 548.33 | 149.62 |
Syria | : | 281.66 | : | : | 6.70 |
Viet Nam | 3411.58 | 5931.71 | 14490.01 | 17583.82 | 11307.23 |
Total | 2321978.91 | 2493518.88 | 2473049.93 | 2432974.82 | 2365772.93 |
Table C.8.
Coconuts, Brazil nuts and cashew nuts, fresh or dried, whether or not shelled or peeled (CN code: 0801) imported in 100 kg into the EU (27) from regions where Nipaecoccus viridis is known to occur (Source: Eurostat accessed on 30/4/2022)
Country | 2016 | 2017 | 2018 | 2019 | 2020 |
---|---|---|---|---|---|
United States | 2447.78 | 1994.95 | 1377.75 | 511.55 | 845.48 |
Mexico | 15.38 | 0.48 | 0.05 | 0.25 | 0.10 |
Laos | : | 0.09 | 280.00 | 0.23 | : |
China | 1409.93 | 1078.20 | 995.67 | 1091.95 | 3073.07 |
Benin | 3230.85 | 2034.22 | 2584.36 | 8774.77 | 11418.80 |
Burkina Faso | 6815.50 | 9277.88 | 9671.97 | 16559.92 | 20808.27 |
Côte d'Ivoire | 211230.31 | 214918.07 | 250187.34 | 222932.19 | 214728.15 |
Egypt | 4.20 | 3.23 | 2.77 | 14.96 | 0.84 |
Kenya | 17.01 | 696.35 | 57.73 | 244.49 | 1191.89 |
Madagascar | 615.99 | 624.94 | 783.06 | 426.35 | 524.37 |
Mauritius | : | : | 8.15 | 1.76 | 0.02 |
Mali | : | 232.21 | 97.80 | 1.00 | 132.01 |
Nigeria | 420.98 | 907.20 | 1694.57 | 3833.89 | 5440.62 |
South Africa | 1.24 | 103.64 | 0.50 | 0.79 | 205.46 |
Seychelles | : | : | 0.15 | ||
Uganda | : | 2.07 | 2.99 | 3.61 | 1.90 |
Senegal | 274.73 | 66.94 | 365.97 | 389.60 | 233.72 |
Togo | 1793.96 | 1514.05 | 2688.34 | 5714.47 | 6346.80 |
Tanzania | 1889.75 | 2570.78 | 1197.66 | 1931.29 | 1800.05 |
Bangladesh | 56.95 | : | : | : | : |
Afghanistan | 0.03 | : | : | : | 0.07 |
Myanmar (Burma) | : | : | 0.15 | : | 10.00 |
Cambodia | : | 0.61 | : | 0.95 | 3.77 |
Japan | : | : | : | : | : |
Jordan | 0.01 | 1.13 | 3.00 | 4.14 | 0.03 |
Iraq | : | 0.02 | : | 10.11 | 23.16 |
India | 170399.32 | 243346.77 | 192497.06 | 205693.06 | 172138.65 |
Israel | 2.40 | 12.32 | 4.95 | 2.36 | 11.16 |
Iran | 5.10 | 1.86 | 2.53 | 8.34 | 11.03 |
Indonesia | 255797.58 | 287011.09 | 302686.51 | 259644.02 | 238720.48 |
Malaysia | 5507.22 | 8394.49 | 4041.78 | 2329.06 | 4411.77 |
Saudi Arabia | 0.24 | 0.04 | : | 0.28 | 0.34 |
Sri Lanka | 129125.94 | 70924.94 | 57516.21 | 76430.03 | 60597.36 |
Australia | 326.68 | 161.34 | 3.97 | 3.09 | 0.02 |
Singapore | 5898.34 | 2475.13 | 3211.06 | 7262.20 | 3843.87 |
Philippines | 368573.57 | 419893.07 | 419609.28 | 398109.92 | 395721.76 |
Thailand | 79261.58 | 78956.34 | 68012.09 | 59013.35 | 35161.23 |
Taiwan | 14.36 | : | 3.40 | : | 0.01 |
Oman | : | 0.02 | : | 0.01 | |
Pakistan | 63.15 | 11.50 | 22.53 | 24.60 | 25.70 |
Syria | 0.60 | 2.23 | 12.37 | 17.80 | 1.25 |
Viet Nam | 761279.37 | 798319.82 | 818389.73 | 967893.87 | 1177974.48 |
New Caledonia | 1.62 | ||||
Total | 2006480.05 | 2145538.00 | 2138013.47 | 2238881.87 | 2355407.70 |
Table C.9.
Cucumbers and gherkins, fresh or chilled (CN code: 0707 00) imported in 100 kg into the EU (27) from regions where Nipaecoccus viridis is known to occur (Source: Eurostat accessed on 30/4/2022)
Country | 2016 | 2017 | 2018 | 2019 | 2020 |
---|---|---|---|---|---|
United States | 9.91 | : | 1.00 | 0.56 | |
Mexico | 6.93 | : | : | 27.04 | |
Laos | : | 0.13 | : | : | : |
China | : | : | 0.70 | : | |
Algeria | 0.50 | 87.32 | 242.36 | 1.00 | : |
Egypt | 916.97 | 1264.14 | 1313.85 | 897.54 | 826.95 |
Kenya | 2.00 | : | : | : | : |
South Africa | 0.01 | 0.55 | : | ||
Uganda | 23.06 | 95.64 | 9.29 | 4.98 | : |
Senegal | 8.00 | : | 2211.76 | : | : |
Sudan | : | : | : | 15.00 | 10.00 |
Bangladesh | 33.61 | 22.55 | 8.79 | 19.40 | 19.55 |
Japan | 3.28 | 6.76 | 4.19 | 18.14 | 6.59 |
Jordan | 7754.88 | 9154.90 | 8897.34 | 10292.92 | 5263.08 |
India | 70.80 | 109.07 | 118.91 | 156.88 | 177.49 |
Israel | 2242.67 | 1756.18 | 1806.98 | 794.48 | 21.04 |
Iran | 188.86 | 1740.91 | 422.80 | 636.46 | 2187.78 |
Indonesia | : | 0.01 | 0.02 | : | : |
Sri Lanka | 0.32 | 1.46 | 8.03 | 5.34 | 6.95 |
Philippines | 0.45 | : | |||
Thailand | 5.25 | 2.89 | 2.04 | 0.93 | 0.03 |
Nepal | 0.01 | : | : | : | : |
Pakistan | : | 6.90 | 12.83 | 12.75 | : |
Syria | : | : | : | : | 38.72 |
Viet Nam | 0.25 | 0.87 | : | : | : |
Total | 11257.39 | 14259.64 | 15059.2 | 12858.52 | 8585.78 |
Table C.10.
Fresh quinces (CN code: 0808 40 00) imported in 100 kg into the EU (27) from regions where Nipaecoccus viridis is known to occur (Source: Eurostat accessed on 30/4/2022)
Country | 2016 | 2017 | 2018 | 2019 | 2020 |
---|---|---|---|---|---|
United States | : | 37.80 | 1.52 | : | : |
China | : | : | : | : | 178.68 |
South Africa | : | : | : | 18.50 | : |
Japan | 1.20 | : | : | : | : |
India | 2.00 | : | : | : | : |
Israel | 181.57 | 382.52 | : | : | 565.35 |
Iran | 7.56 | : | : | : | 21.75 |
Total | 192.33 | 420.32 | 1.52 | 18.5 | 765.78 |
Table C.11.
Fresh persimmons (CN code: 0810 70 00) imported in 100 kg into the EU (27) from regions where Nipaecoccus viridis is known to occur (Source: Eurostat accessed on 30/4/2022)
Country | 2016 | 2017 | 2018 | 2019 | 2020 |
---|---|---|---|---|---|
China | 17.57 | : | 5.09 | : | 17.40 |
South Africa | 823.16 | 817.79 | 206.08 | 7857.42 | 4974.49 |
Afghanistan | : | : | : | : | 22.95 |
Japan | : | 0.27 | 0.76 | 0.27 | 0.02 |
Israel | 2404.45 | 3231.29 | 1158.64 | 181.58 | 3211.13 |
Thailand | : | : | 0.07 | : | : |
Pakistan | : | : | : | 0.52 | : |
Viet Nam | : | : | : | : | 0.01 |
Total | 3245.18 | 4049.35 | 1370.64 | 8039.79 | 8226 |
Table C.12.
Fresh figs (CN code: 0804 20) imported in 100 kg into the EU (27) from regions where Nipaecoccus viridis is known to occur (Source: Eurostat accessed on 30/4/2022)
Country | 2016 | 2017 | 2018 | 2019 | 2020 |
---|---|---|---|---|---|
United States | : | : | : | 0.04 | : |
Mexico | 79.83 | 189.76 | 153.89 | 118.92 | 94.08 |
Laos | : | 3.26 | : | : | : |
Algeria | 10.00 | 20.93 | 8.12 | 1.50 | : |
Egypt | 7.46 | 10.53 | 13.41 | 44.08 | 60.26 |
Kenya | 0.10 | ||||
South Africa | 493.50 | 697.57 | 624.33 | 464.30 | 471.60 |
Zimbabwe | 0.00 | : | : | : | : |
Jordan | 4.69 | : | 3.72 | 5.53 | 4.68 |
Iraq | : | : | : | : | : |
India | 145.14 | 59.70 | 15.48 | 20.64 | 7.96 |
Israel | 2316.88 | 1300.18 | 1406.99 | 859.53 | 604.66 |
Iran | : | : | 0.07 | : | 4.95 |
Saudi Arabia | : | 0.05 | : | : | : |
Sri Lanka | : | 0.40 | : | 93.87 | : |
Viet Nam | : | : | : | 0.02 | |
Papua New Guinea | : | 0.18 | : | : | : |
Total | 3057.5 | 2282.66 | 2226.01 | 1608.41 | 1248.21 |
Table C.13.
Fresh apples (CN code 0808 10) imported in 100 kg into the EU (27) from regions where Nipaecoccus viridis is known to occur (Source: Eurostat accessed on 30/4/2022)
Country | 2016 | 2017 | 2018 | 2019 | 2020 |
---|---|---|---|---|---|
United States | 0.05 | 545.82 | 2874.22 | : | : |
China | 13188.53 | 1644.89 | 15539.34 | 780.15 | 4778.37 |
Algeria | 856.80 | : | : | 4.66 | : |
Egypt | 3161.05 | 3234.13 | 2299.68 | : | 2501.73 |
Mauritius | : | : | : | 1.32 | : |
Nigeria | : | 0.76 | : | : | : |
South Africa | 298162.64 | 252068.96 | 334615.90 | 258077.03 | 329086.35 |
Zambia | : | : | 205.80 | : | : |
Uganda | : | : | 0.15 | : | : |
Bangladesh | : | 2.64 | 2.18 | 0.63 | 4.05 |
Japan | 7.61 | 0.53 | 0.95 | : | 19.25 |
Jordan | 572.72 | : | : | 206.52 | : |
India | 0.01 | : | : | : | 0.45 |
Israel | 2225.55 | 1037.58 | 936.63 | 1813.20 | 755.03 |
Iran | : | : | 2945.28 | 0.38 | 676.65 |
Sri Lanka | : | : | : | 0.15 | : |
Australia | 1048.66 | 4926.09 | 9159.46 | 8311.03 | 3638.72 |
Singapore | 211.68 | : | : | : | : |
Thailand | : | 3.79 | : | : | : |
Taiwan | : | : | : | 2.97 | : |
Pakistan | : | : | : | 1.95 | 0.08 |
Syria | : | : | 585.00 | : | : |
Viet Nam | : | : | 0.20 | : | : |
Total | 319435.30 | 263465.19 | 369164.79 | 269199.99 | 341460.68 |
Table C.14.
Fresh or dried guavas, mangoes and mangosteens (CN code 0804 50 00) imported in 100 kg into the EU (27) from regions where Nipaecoccus viridis is known to occur (Source: Eurostat accessed on 30/04/2022
Country | 2016 | 2017 | 2018 | 2019 | 2020 |
---|---|---|---|---|---|
United States | 78874.11 | 45478.21 | 54660.34 | 82580.54 | 82852.21 |
Mexico | 35095.07 | 40848.36 | 46001.68 | 50935.79 | 51841.89 |
Angola | : | : | 486.65 | 658.15 | 351.50 |
Laos | 753.34 | 620.36 | 603.14 | 806.50 | 525.32 |
China | 38.95 | 51.87 | 180.81 | 78.23 | 104.34 |
Benin | 26.40 | : | : | 226.79 | |
Burkina Faso | 62078.35 | 45732.84 | 52399.48 | 65354.19 | 64404.44 |
Comoros | : | : | : | 94.92 | |
Côte d'Ivoire | 229117.62 | 268109.01 | 278429.74 | 281610.27 | 230154.91 |
Egypt | 4135.64 | 9186.69 | 4855.57 | 6407.46 | 12233.16 |
Kenya | 232.06 | 4.08 | 65.09 | 10.30 | 66.53 |
Madagascar | 246.94 | 22.10 | 15.02 | 0.66 | 1.05 |
Mali | 72965.87 | 53045.00 | 68743.59 | 91829.06 | 85458.70 |
Malawi | : | : | : | : | 648.00 |
Nigeria | 0.78 | 0.10 | 1.13 | 1.95 | 0.03 |
South Africa | 8550.13 | 13015.45 | 9739.99 | 12116.95 | 8656.28 |
Zambia | : | 2.46 | : | : | 23.04 |
Uganda | 257.30 | 452.71 | 360.01 | 662.25 | 389.56 |
Senegal | 97669.02 | 114177.24 | 147536.88 | 125252.79 | 88969.02 |
Togo | 39.19 | 58.16 | 57.86 | 221.65 | 40.00 |
Sudan | 34.71 | 43.30 | 215.93 | 29.99 | 10.00 |
Tanzania | : | : | 0.50 | 1.14 | : |
Bangladesh | 438.53 | 256.66 | 331.27 | 310.73 | 323.91 |
Myanmar (Burma) | : | 0.28 | 1.47 | 1.00 | : |
Cambodia | 883.47 | 2098.02 | 2164.17 | 1533.79 | 904.49 |
Japan | 0.66 | : | : | : | 0.01 |
Jordan | 4.00 | : | : | : | : |
India | 5989.34 | 8148.87 | 9470.36 | 9315.51 | 7347.61 |
Israel | 143726.08 | 140551.30 | 108353.48 | 121875.16 | 98143.59 |
Iran, Islamic Republic of | 15.65 | 12.12 | 3.00 | 9.10 | 1.56 |
Indonesia | 1981.20 | 2004.36 | 2926.64 | 2386.27 | 1406.94 |
Malaysia | 289.86 | 197.22 | 170.64 | 72.72 | 44.56 |
Saudi Arabia | 0.10 | 0.69 | 95.05 | : | 0.18 |
Sri Lanka | 1254.27 | 1003.35 | 765.31 | 813.83 | 423.16 |
Australia | 25.72 | 94.18 | 62.92 | : | : |
Singapore | 1.20 | : | : | 0.23 | 0.15 |
Philippines | 1028.05 | 519.88 | 795.56 | 368.97 | 128.10 |
Thailand | 6460.81 | 7401.80 | 6911.89 | 6743.92 | 5260.84 |
Taiwan | : | : | 3.48 | 17.34 | 0.92 |
Oman | : | : | : | 223.93 | |
Pakistan | 17149.78 | 15912.58 | 21867.43 | 29207.33 | 16196.50 |
Viet Nam | 794.89 | 950.37 | 1346.64 | 1546.69 | 965.31 |
Guam | : | : | : | : | 224.00 |
Total | 770132.69 | 770026.02 | 819622.72 | 893079.31 | 758328.60 |
Table C.15.
Fresh or chilled olives (excl. for oil production) (CN code 0709 92) imported in 100 kg into the EU (27) from regions where Nipaecoccus viridis is known to occur (Source: Eurostat accessed on 30/04/2022
Country | 2016 | 2017 | 2018 | 2019 | 2020 |
---|---|---|---|---|---|
Egypt | : | : | : | 21.16 | 130.13 |
South Africa | : | : | : | 0.09 | : |
Bangladesh | 9.90 | 15.44 | 23.98 | 11.70 | 11.10 |
Jordan | 63.51 | 3.50 | 9.06 | 57.58 | : |
Saudi Arabia | : | : | : | : | 0.05 |
Total | 73.41 | 18.94 | 33.04 | 90.53 | 141.28 |
Table C.16.
Fresh or dried avocados (excl. for oil production) (CN code 0804 40 00) imported in 100 kg into the EU (27) from regions where Nipaecoccus viridis is known to occur (Source: Eurostat accessed on 30/04/2022
Country | 2016 | 2017 | 2018 | 2019 | 2020 |
---|---|---|---|---|---|
United States | 8819.53 | 1.19 | 2546.86 | 0.02 | 4.66 |
Mexico | 503687.52 | 445611.06 | 463741.28 | 767878.48 | 716092.02 |
Angola | : | : | 3.85 | : | 3.54 |
China | 193.97 | 35.28 | : | 1.23 | 0.04 |
Côte d'Ivoire | 8.15 | 18.26 | 230.36 | 72.20 | 68.24 |
Egypt | 211.20 | 5.35 | 4.58 | 79.92 | 363.95 |
Kenya | 228426.16 | 243947.31 | 404593.87 | 346231.90 | 435308.72 |
Madagascar | : | : | : | : | 0.96 |
Mauritius | 124.44 | 36.13 | 42.27 | 24.28 | 15.23 |
Nigeria | 1.06 | 3.15 | 3.18 | 0.51 | : |
South Africa | 419768.89 | 315854.56 | 652817.98 | 401352.79 | 416290.22 |
Zambia | : | : | 53.68 | : | |
Rwanda | 2.75 | 125.33 | 225.09 | 216.44 | 153.67 |
Uganda | 1912.57 | 2195.25 | 2233.81 | 3364.25 | 3575.68 |
Senegal | |||||
Togo | 11.76 | 7.87 | 12.89 | 1.42 | 57.15 |
Tanzania | 26823.05 | 25773.58 | 55517.16 | 60480.96 | 50769.74 |
Zimbabwe | 13030.06 | 20378.85 | 36539.24 | 32020.52 | 38872.63 |
India | 0.04 | 2.06 | 0.52 | 0.06 | : |
Israel | 301123.91 | 424267.97 | 370378.23 | 437318.01 | 345664.24 |
Malaysia | 0.03 | : | 47.04 | : | : |
Saudi Arabia | : | 0.05 | 0.06 | ||
Sri Lanka | 7.03 | 4.88 | 5.63 | 2.00 | 11.95 |
Australia | : | : | : | 0.01 | : |
Philippines | : | : | : | : | 0.05 |
Thailand | 3.68 | 9.76 | 9.66 | 9.06 | 3.39 |
Viet Nam | 1.00 | : | : | 0.05 | : |
New Caledonia | : | : | : | 2.09 | : |
Total | 1504156.80 | 1478277.89 | 1989007.18 | 2049056.26 | 2007256.08 |
Table C.17.
Fresh pears (CN code 0808 30) imported in 100 kg into the EU (27) from regions where Nipaecoccus viridis is known to occur (Source: Eurostat accessed on 30/04/2022
Country | 2016 | 2017 | 2018 | 2019 | 2020 |
---|---|---|---|---|---|
United States | 214.47 | 454.76 | 471.49 | 12.54 | : |
China | 102076.61 | 98191.53 | 116993.12 | 82741.84 | 99293.92 |
Egypt | : | 31.50 | 0.90 | : | 225.00 |
Nigeria | : | : | 1.00 | : | 0.36 |
South Africa | 865862.63 | 759193.32 | 655428.91 | 590939.08 | 583331.56 |
Afghanistan | : | : | : | 225.00 | : |
Japan | 2.50 | 0.02 | 0.45 | : | : |
Israel | : | 664.59 | : | 569.20 | 219.49 |
Iran | : | : | 32.40 | : | 7.50 |
Australia | : | : | 1224.72 | : | : |
Total | 968156.21 | 858535.72 | 774152.99 | 674487.66 | 683077.83 |
Table C.18.
Tomatoes, fresh or chilled (CN code 0702 00 00) imported in 100 kg into the EU (27) from regions where Nipaecoccus viridis is known to occur (Source: Eurostat accessed on 30/04/2022
Country | 2016 | 2017 | 2018 | 2019 | 2020 |
---|---|---|---|---|---|
United States | : | : | 0.11 | 0.04 | 0.13 |
Mexico | : | : | : | : | 0.80 |
Angola | : | 0.18 | : | : | : |
Algeria | 30.45 | 27.56 | 161.85 | 461.62 | : |
Côte d'Ivoire | : | : | 0.10 | : | : |
Egypt | 9135.43 | 14023.94 | 15102.55 | 18876.68 | 9491.42 |
Madagascar | 7.31 | : | 40.00 | : | : |
Uganda | 0.12 | : | : | : | |
Senegal | 91850.25 | 62281.26 | 85804.22 | 77820.16 | 74513.76 |
Japan | 13.75 | 8.98 | 13.31 | 45.67 | 34.37 |
Jordan | 364.60 | : | 208.35 | 21.60 | 151.41 |
India | : | : | : | 0.01 | |
Israel | 16739.21 | 10861.22 | 6392.59 | 782.65 | 138.00 |
Iran | : | 363.79 | : | : | 11.13 |
Australia | : | : | : | 2.52 | : |
Thailand | 0.08 | 0.08 | 0.08 | 0.02 | 0.02 |
Oman | : | : | : | : | 1.27 |
Viet Nam | 0.03 | 0.06 | : | : | |
Total | 118141.1 | 87567.19 | 107723.2 | 98010.97 | 84342.31 |
Table C.19.
Fresh or chilled aubergines “eggplants” (CN code 0709 30 00) imported in 100 kg into the EU (27) from regions where Nipaecoccus viridis is known to occur (Source: Eurostat accessed on 30/04/2022
Country | 2016 | 2017 | 2018 | 2019 | 2020 |
---|---|---|---|---|---|
United States | : | 18.21 | : | 28.58 | : |
Mexico | 24.15 | 2350.17 | 7799.81 | 8442.93 | 6853.17 |
Laos | 623.61 | 507.16 | 553.87 | 651.54 | 575.33 |
China | : | : | : | 0.60 | : |
Algeria | : | 5.61 | 116.97 | 44.96 | : |
Burkina Faso | 2202.53 | 3908.14 | 2339.70 | 1624.25 | 5115.89 |
Côte d'Ivoire | 92.94 | 37.29 | 82.48 | 170.41 | 22.06 |
Egypt | 1368.59 | 1565.41 | 639.54 | 848.70 | 925.13 |
Kenya | 1269.52 | 1081.58 | 799.63 | 885.61 | 1261.94 |
Madagascar | 5.66 | : | : | 2.00 | 5.57 |
Mali | 897.30 | 800.80 | 96.00 | : | : |
Nigeria | 2.42 | 2.86 | 0.10 | : | : |
South Africa | 307.77 | 344.95 | 366.46 | 506.53 | 288.94 |
Rwanda | 3.54 | 16.08 | 53.41 | 84.53 | 75.88 |
Uganda | 4208.96 | 2094.76 | 3355.55 | 4873.36 | 5174.39 |
Senegal | 717.75 | 714.68 | 665.41 | 697.04 | 1369.92 |
Togo | 341.04 | 322.22 | 309.84 | 278.08 | 269.06 |
Sudan | 10.61 | 10.00 | |||
Tanzania | : | : | : | 0.24 | : |
Bangladesh | 0.15 | 1.05 | : | : | : |
Cambodia | 6.81 | 10.77 | 13.77 | 37.58 | 140.51 |
Japan | 0.24 | 1.24 | 0.53 | 1.94 | 0.38 |
Jordan | 1948.59 | 2825.54 | 2293.48 | 1460.50 | 795.80 |
India | 13.83 | 4.45 | : | 15.61 | 3.25 |
Israel | 706.70 | 1184.07 | 628.52 | 327.60 | 146.58 |
Iran, Islamic Republic of | : | 5.80 | : | 14.00 | : |
Indonesia | : | : | 0.21 | 2.93 | 10.35 |
Malaysia | 319.24 | 368.87 | 253.99 | 213.25 | 7.29 |
Sri Lanka | 10.30 | 6.57 | 0.35 | 23.51 | 15.29 |
Philippines | : | : | : | 0.86 | |
Thailand | 371.71 | 361.70 | 392.81 | 482.10 | 435.44 |
Pakistan | 0.40 | : | 3.85 | 0.48 | 10.60 |
Syria | : | 1.00 | : | 2.88 | 118.22 |
Viet Nam | 439.72 | 375.63 | 338.35 | 307.70 | 38.43 |
Total | 15883.47 | 18916.61 | 21104.63 | 22040.91 | 23669.42 |
Table C.20.
Potatoes, fresh or chilled (CN code 0701) imported in 100 kg into the EU (27) from regions where Nipaecoccus viridis is known to occur (Source: Eurostat accessed on 30/04/2022
Country | 2016 | 2017 | 2018 | 2019 | 2020 |
---|---|---|---|---|---|
United States | 1.53 | 62.76 | 10.88 | 60.62 | 37.07 |
Mexico | 0.05 | : | 0.14 | 1.04 | |
Laos | : | 0.26 | : | : | : |
China | 0.09 | 5.00 | : | : | 0.43 |
Algeria | 5612.00 | 2489.60 | 5089.34 | 6643.02 | 9440.93 |
Côte d'Ivoire | 9.95 | ||||
Egypt | 1488601.48 | 2118574.29 | 1737561.60 | 2887875.53 | 2537298.72 |
Madagascar | 136.52 | 21.39 | 35.05 | 21.54 | 34.00 |
Mali | : | : | 8.45 | ||
Nigeria | : | : | 0.70 | 1.75 | |
South Africa | 2.00 | : | : | 235.95 | : |
Zambia | : | 135.66 | : | : | : |
Rwanda | : | : | 11.73 | : | |
Uganda | 15.15 | 36.06 | 4.35 | 7.01 | 6.20 |
Senegal | 0.02 | : | : | : | : |
Togo | : | 14.02 | 27.11 | 4.58 | : |
Japan | : | 0.01 | : | : | : |
Jordan | : | : | : | : | 2362.37 |
India | 0.01 | : | : | : | : |
Israel | 1366623.28 | 1311430.16 | 1257417.27 | 1303937.89 | 993329.82 |
Indonesia | : | 0.02 | : | : | 0.69 |
Saudi Arabia | : | 1300.00 | 2630.00 | 1085.00 | : |
Sri Lanka | : | : | : | 0.23 | 1.24 |
Thailand | : | 0.05 | 2.05 | 0.60 | : |
Taiwan | : | : | 0.71 | : | : |
Syria | : | : | 275.00 | : | : |
Viet Nam | : | : | : | 1.95 | : |
New Caledonia | : | : | 0.39 | : | : |
Total | 2860992.13 | 3434079.23 | 3003073.93 | 4199874.76 | 3542514.26 |
Table C.21.
Grapes, fresh or dried (CN code 0806) imported in 100 kg into the EU (27) from regions where Nipaecoccus viridis is known to occur (Source: Eurostat accessed on 30/04/2022
Country | 2016 | 2017 | 2018 | 2019 | 2020 |
---|---|---|---|---|---|
United States | 191784.90 | 211054.06 | 106691.73 | 95559.91 | 114324.74 |
Mexico | : | 358.96 | : | 186.71 | 184.66 |
Angola | : | : | 0.18 | 0.80 | |
China | 125769.00 | 47957.90 | 87690.22 | 191986.55 | 156789.04 |
Algeria | : | : | 0.50 | 17.17 | 313.02 |
Côte d'Ivoire | 200.00 | : | : | : | : |
Egypt | 330566.05 | 404802.55 | 429995.18 | 442801.07 | 463301.46 |
Kenya | : | : | 186.96 | : | : |
Madagascar | : | : | 0.08 | : | : |
Mauritius | 0.02 | 0.14 | : | : | 2.22 |
South Africa | 1512476.18 | 1620130.63 | 1703622.95 | 1649404.49 | 1757286.30 |
Zambia | 0.00 | 0.28 | 0.03 | : | : |
Bangladesh | 1.05 | : | 0.50 | : | : |
Afghanistan | 7469.52 | 5780.98 | 24929.08 | 31135.09 | 24701.15 |
Japan | 6.03 | 4.37 | 1.52 | 1.19 | 21.09 |
Jordan | 1.15 | : | 0.36 | : | : |
Iraq | : | 7.68 | 12.20 | 7.82 | 49.96 |
India | 701938.16 | 849117.89 | 741303.06 | 970130.19 | 767803.65 |
Israel | 13171.80 | 7365.66 | 6433.57 | 320.43 | 1083.52 |
Iran | 178916.63 | 146040.55 | 101488.05 | 165329.68 | 201689.92 |
Indonesia | : | : | : | : | 1.92 |
Saudi Arabia | 0.00 | 1.51 | 45.00 | 0.04 | 0.01 |
Sri Lanka | : | : | 0.00 | : | : |
Australia | 30009.97 | 24989.40 | 28005.60 | 24170.86 | 18763.02 |
Singapore | 4.34 | 603.53 | 3.49 | 1.75 | 3.66 |
Philippines | 0.48 | : | : | : | : |
Thailand | 1.63 | 92.32 | 4.46 | 0.87 | 1.38 |
Oman | 0.00 | : | : | : | 0.00 |
Pakistan | 6148.97 | 10762.89 | 14655.68 | 13385.60 | 11092.98 |
Syria | 0.25 | : | 2.10 | 2.73 | 2.73 |
Viet Nam | : | 0.00 | : | 0.00 | 10.14 |
Total | 3098466.13 | 3329071.30 | 3245072.50 | 3584442.95 | 3517426.57 |
Notifications of interceptions of harmful organisms began to be compiled in Europhyt in May 1994 and in TRACES in May 2020. As at 1 December 2022, there were 0 records of interception of N. viridis in the Europhyt and TRACES databases.
In the UK, there were 35 interceptions of N. viridis between 2002 and 2018, mostly on fresh Citrus fruits from Bangladesh. In almost all cases this was Citrus macroptera, commonly known as Bangladeshi lemons, Jara lemons, wild oranges and Shatkora, and frequently misidentified as lemon or lime in trade. N. viridis was also found on Annona fruits from India and Pakistan, citrus fruits from Pakistan and Thailand, Citrus hystrix leaves from Thailand, guava fruits from Pakistan, mango fruits from India and Pakistan, and fresh Houttuynia leaves (edible and medicinal herb) from Laos. In several cases, the plant material was heavily infested with mealybugs (Fera unpublished records). No action was taken against these findings and so no notifications were made to Europhyt.
3.4.2. Establishment
Is the pest able to become established in the EU territory?
Yes, N. viridis could establish in parts of the EU territory as there are climatic conditions that are similar to those in areas where the pest occurs, and potential hosts are present.
The area of the EU most suitable for establishment is in the southern EU around the Mediterranean Sea.
Unless moved with plants for planting, there are uncertainties over the pests’ ability to transfer to a suitable host following arrival into the EU. However, the high polyphagy of this mealybug could increase the changes of successful transfer even for colonies on fruit, vegetables, or cut flowers. Uncertainties also include its ability to find a mate and other Allee effects (effects causing reduced survival of new colonies with a small number of individuals) (Tobin et al., 2011) as well as the impact of natural enemies in the EU.
3.4.2.1. EU distribution of main host plants
N. viridis 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, apples, apricots, asparagus, avocados, celery, citrus, cucumbers, eggplants, figs, grapes, olives, pears, tomatoes and ornamental plants are important crops in the EU.
Table 5.
Harvested area of important N. viridis hosts in EU 27, 2016‐2020 (thousand ha) (Eurostat accessed on 13 June 2022)
Crop | Eurostat code | 2016 | 2017 | 2018 | 2019 | 2020 |
---|---|---|---|---|---|---|
Olives | O1000 | 5,043.87 | 5,056.93 | 5,098.62 | 5,071.59 | 5,106.54 |
Grapes | W1000 | 3,136.15 | 3,133.32 | 3,135.50 | 3,155.20 | 3,156.21 |
Citrus fruits | T0000 | 519.01 | 502.84 | 508.99 | 512.83 | 519.98 |
Apples | F1110 | 505.66 | 504.61 | 506.27 | 491.08 | 482.99 |
Tomatoes | V3100 | 253.95 | 247.95 | 239.48 | 242.52 | 233.19 |
Pears | F1120 | 115.13 | 113.81 | 113.54 | 110.66 | 107.04 |
Apricots | F1230 | 72.52 | 72.23 | 72.57 | 73.22 | 76.12 |
Asparagus | V2600 | 56.42 | 59.05 | 60.04 | 58.94 | 59.10 |
Cucumbers | V3200 | 32.34 | 31.81 | 32.65 | 33.70 | 27.78 |
Figs | F2100 | 23.74 | 24.63 | 24.99 | 25.59 | 27.21 |
Eggplants | V3410 | 21.48 | 20.73 | 21.24 | 20.61 | 21.14 |
Avocados | F2300 | 12.24 | 12.72 | 13.22 | 17.50 | 19.63 |
Celery | V2200 | 7.42 | 7.65 | : | : | : |
‘:’ data not available.
3.4.2.2. Climatic conditions affecting establishment
N. viridis occurs mainly in tropical and subtropical regions in Asia, Africa and Oceania. It has been present in Egypt for more than a hundred years and has recently been found in Turkey. The thermal biology of this pest is little studied and no temperature thresholds for development have been reported. Consequently, there is some uncertainty regarding the climatic requirements of the pest. Figure 3 shows the world distribution of Köppen–Geiger climate types (Kottek et al., 2006) that occur in the EU and which occur in countries where N. viridis has been reported. Southern EU countries may provide suitable climatic conditions for the establishment of N. viridis. As a tropical and sub‐tropical organism, low temperatures, as indicated by frost, may limit establishment. Figure 4 shows frost free areas in the EU which could perhaps be colonised by N. viridis. Data for Figure 4 represents the 30‐year period 1988–2017 and was sourced from the Climatic Research Unit high resolution gridded dataset CRU TS v. 4.03 at 0.5° resolution (https://crudata.uea.ac.uk/cru/data/hrg/).
Figure 3.
World distribution of selected Köppen–Geiger climate types which occur in the EU and in countries where Nipaecoccus viridis has been reported. Yellow dots indicate precise records for N. viridis
Figure 4.
Annual frost days in the world (mean 1988–2017) (source: Climatic Research Unit, University of East Anglia, UK)
Establishment outdoors in central and northern Europe is very unlikely. Nevertheless, there is a possibility that N. viridis could occur in greenhouses and on indoor plantings in such areas. The congeneric coconut mealybug or spiked mealybug N. nipae (Maskell) is well established in botanic greenhouses in Europe.
3.4.3. Spread
Describe how the pest would be able to spread within the EU territory following establishment?
Natural spread by first instar nymphs crawling or being carried by wind, other animals, or machinery, will occur locally and relatively slowly. All stages may be moved over long distances in trade of infested plant materials, specifically plants for planting, fruits, vegetables, and cut flowers.
Comment on plants for planting as a mechanism of spread. Plants for planting provide the main spread mechanism for N. viridis over long distances.
First instar nymphs may move to neighbouring plants by crawling or be passively dispersed by wind or hitchhiking on clothing, equipment or animals (Kondo and Watson, 2022). The wax forming the ovisac is sticky and can be drawn out into a string when touched. When samples are handled in the laboratory, parts of the ovisac with eggs can easily stick to and be spread on equipment. It is not known if eggs can be spread this way in nature.
Plants for planting, fruits, vegetables and cut flowers are the main pathways of spread of N. viridis over long distances.
3.5. Impacts
Would the pests’ introduction have an economic or environmental impact on the EU territory?
Yes, if N. viridis established in the EU, it would most probably have an economic impact.
N. viridis feeds on phloem sap, weakening the host plant. It egests sugary honeydew on which sooty moulds develop, which can interfere with photosynthesis, reducing market value of nursery stock and fruits. It is known as a pest of avocado, citrus, cotton, mango, soursop, and stored potatoes (Kondo and Watson, 2022). It has recently been found in commercial citrus orchards in Florida (USA), where it is having a significant impact (Diepenbrock and Ahmed, 2020). Infestations have been documented both in mature citrus groves with damage to fruit, and in young, replanted trees. Feeding damage includes distorted fruit and leaves, branch dieback, and even tree death in young, recently planted trees. The recent introduction in Florida of exclusion bags on newly planted citrus trees to prevent access by Asian citrus psyllid (Diaphorina citri Kuwayama (Hemiptera: Psyllidae)), the vector of the pathogen associated with citrus greening disease, has exacerbated the impact of the mealybug because natural enemies were also excluded (Diepenbrock and Ahmed, 2020). N. viridis was a serious pest of citrus and Ziziphus in Jordan in the 1980s, and infestations could result in total crop loss. However, the release of the biocontrol agent A. agraensis (= A. indicus Shafee, Alam and Agarwal) has resulted in good control of the mealybug (Williams, 2004). N. viridis is one of the main pests of mango in Okinawa, Japan, and a pest of stored potatoes and cotton in Asia (Williams, 2004).
N. viridis has a wide host range including many economically important crops and ornamentals grown in the EU (listed in Section 3.1.3) but there appear to be no published records of harmful impacts to many of these plants.
There seem to be suitable areas in the EU, where N. viridis could become abundant and harmful, particularly in the southern EU around the Mediterranean.
3.6. 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 N. viridis, they mitigate the likelihood of its entry, establishment and spread within the EU (see also Section 3.6.1).
3.6.1. Identification of potential additional measures
Phytosanitary measures (prohibitions) are currently applied to some host plants for planting (see 3.3.2).
Additional potential risk reduction options and supporting measures are shown in sections 3.6.1.1. and 3.6.1.2.
3.6.1.1. 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, Blue = WIP) | RRO summary | Risk element targeted (entry/establishment/spread/impact) |
---|---|---|
Require pest freedom | Pest free place of production (e.g. place of production and its immediate vicinity is free from pest over an appropriate time period, e.g. since the beginning of the last complete cycle of vegetation, or past 2 or 3 cycles). Pest free production site. | Entry/Spread/Impact |
Growing plants in isolation | Place of production is insect proof originate in a place of production with complete physical isolation E.g. a dedicated structure such as glass or plastic greenhouses producing vegetables or flowers. | Entry/Spread |
Managed growing conditions | Used to mitigate likelihood of infestation at origin. Plants collected directly from natural habitats, have been grown, held and trained for at least a year prior to dispatch in officially registered nurseries, which are subject to an officially supervised control regime. | Entry/Spread |
Biological control and behavioural manipulation | There is an extensive list of natural enemies recorded for N. viridis (Kondo and Watson, 2022) and it has been successfully controlled in Jordan by the release of A. agraensis. In southern India, it is controlled by the parasitoid Anagyrus dactylopii (Howard) (Hymenoptera: Encyrtidae) and the predator Domomyza perspicax (Knab) (= Gitona perspicax) (Diptera: Drosophilidae) (Kondo and Watson, 2022). | Spread/Impact |
Chemical treatments on crops including reproductive material | Chemical control of Nipaecoccus spp. is discussed by Kondo and Watson (2022). | Entry/Establishment/Spread/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 relevant treatments addressed in this information sheet are:
|
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. | 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. | Spread |
Heat and cold treatments | Controlled temperature treatments aimed to kill or inactivate pests without causing any unacceptable prejudice to the treated material itself. | Entry/Spread |
3.6.1.2. 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 measure (Blue underline = Zenodo doc, Blue = WIP) | Summary | Risk 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. |
Entry/Establishment/Spread/Impact |
Laboratory testing | Examination, other than visual, to determine if pests are present using official diagnostic protocols. Diagnostic protocols describe the minimum requirements for reliable diagnosis of regulated pests. | Entry/Spread |
Sampling |
According to ISPM 31, it is usually not feasible to inspect entire consignments, so phytosanitary inspection is performed mainly on samples obtained from a consignment. It is noted that the sampling concepts presented in this standard may also apply to other phytosanitary procedures, notably selection of units for testing. For inspection, testing and/or surveillance purposes the sample may be taken according to a statistically based or a non‐statistical sampling methodology. |
Entry |
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)
|
Entry/Spread |
Certified and approved premises | Mandatory/voluntary certification/approval of premises is a process including a set of procedures and of actions implemented by producers, conditioners and traders contributing to ensure the phytosanitary compliance of consignments. It can be a part of a larger system maintained by the NPPO in order to guarantee the fulfilment of plant health requirements of plants and plant products intended for trade. Key property of certified or approved premises is the traceability of activities and tasks (and their components) inherent the pursued phytosanitary objective. Traceability aims to provide access to all trustful pieces of information that may help to prove the compliance of consignments with phytosanitary requirements of importing countries. | Entry/Spread |
Certification of reproductive material (voluntary/official) | Plants come from within an approved propagation scheme and are certified pest free (level of infestation) following testing; Used to mitigate against pests that are included in a certification scheme. | Entry/Spread |
Delimitation of Buffer zones | ISPM 5 defines a buffer zone as “an area surrounding or adjacent to an area officially delimited for phytosanitary purposes in order to minimise the probability of spread of the target pest into or out of the delimited area, and subject to phytosanitary or other control measures, if appropriate” (ISPM 5). The objectives for delimiting a buffer zone can be to prevent spread from the outbreak area and to maintain a pest free production place (PFPP), site (PFPS) or area (PFA). | Spread |
Surveillance | Surveillance for early detection of outbreaks | Entry/Spread |
3.6.1.3. Biological or technical factors limiting the effectiveness of measures
N. viridis is polyphagous, making the inspections of all consignments containing hosts from countries where the pest occurs difficult.
Limited effectiveness of contact insecticides due to the presence of protective wax cover
Difficulty in detecting early infestations
3.7. Uncertainty
No key uncertainties of the assessment have been identified.
4. Conclusions
N. viridis satisfies all the criteria that are within the remit of EFSA to assess for it to be regarded as a potential Union quarantine pest (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 categorisation | Panel's conclusions against criterion in Regulation (EU) 2016/2031 regarding Union quarantine pest | Key uncertainties |
---|---|---|
Identity of the pest (Section 3.1 ) | The identity of N. viridis is established. Taxonomic keys based on morphology of adults exist. There are also molecular techniques for species identification. | None |
Absence/presence of the pest in the EU (Section 3.2 ) | No, N. viridis is not known to occur in the EU. | None |
Pest potential for entry, establishment and spread in the EU (Section 3.4 ) |
N. viridis is able to enter, become established and spread within the EU territory especially in the southern EU MS. The main pathways for entry are plants for planting, cut flowers, fruits, and vegetables. |
None |
Potential for consequences in the EU (Section 3.5 ) |
The introduction of the pest could cause yield and quality losses on several crops and reduce the value of ornamental plants. | None |
Available measures (Section 3.6 ) |
There are measures available to prevent entry, establishment and spread of N. viridis in the EU. Risk reduction options include inspections, chemical and physical treatments on consignments of fresh plant material from infested countries and the production of plants for import in the EU in pest free areas. |
None |
Conclusion (Section 4 ) | N. viridis satisfies all the criteria that are within the remit of EFSA to assess for it to be regarded as a potential Union quarantine pest | |
Aspects of assessment to focus on/scenarios to address in future if appropriate: |
Abbreviations
- EPPO
European and Mediterranean Plant Protection Organization
- FAO
Food and Agriculture Organization
- IPPC
International Plant Protection Convention
- ISPM
International Standards for Phytosanitary Measures
- MS
Member State
- PLH
EFSA Panel on Plant Health
- PZ
Protected Zone
- TFEU
Treaty on the Functioning of the European Union
- ToR
Terms of Reference
Glossary
- Containment (of a pest)
Application of phytosanitary measures in and around an infested area to prevent spread of a pest (FAO, 2021).
- Control (of a pest)
Suppression, containment or eradication of a pest population (FAO, 2021).
- Entry (of a pest)
Movement of a pest into an area where it is not yet present, or present but not widely distributed and being officially controlled (FAO, 2021).
- Eradication (of a pest)
Application of phytosanitary measures to eliminate a pest from an area (FAO, 2021).
- Establishment (of a pest)
Perpetuation, for the foreseeable future, of a pest within an area after entry (FAO, 2021).
- Greenhouse
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.
- Hitchhiker
An organism sheltering or transported accidentally via inanimate pathways including with machinery, shipping containers and vehicles; such organisms are also known as contaminating pests or stowaways (Toy and Newfield, 2010).
- Impact (of a pest)
The impact of the pest on the crop output and quality and on the environment in the occupied spatial units.
- Introduction (of a pest)
The entry of a pest resulting in its establishment (FAO, 2021).
- Pathway
Any means that allows the entry or spread of a pest (FAO, 2021).
- Phytosanitary measures
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, 2021).
- Quarantine pest
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, 2021).
- Risk reduction option (RRO)
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.
- Spread (of a pest)
Expansion of the geographical distribution of a pest within an area (FAO, 2021).
Appendix A – Nipaecoccus viridis host plants/species affected
Source: CABI (online) and García Morales et al. (2016)
Host status | Host name | Plant family | Common name | References |
---|---|---|---|---|
Cultivated hosts | Abelmoschus | Malvaceae | – | García Morales et al. (2016) |
Abelmoschus esculentus | Malvaceae | Lady's fingers | García Morales et al. (2016) | |
Abelmoschus manihot | Malvaceae | Hibiscus root | García Morales et al. (2016) | |
Abrus | Fabaceae | – | García Morales et al. (2016) | |
Abrus precatorius | Fabaceae | Rosary pea | CABI (online) | |
Acacia | Fabaceae | – | García Morales et al. (2016) | |
Acacia modesta | Fabaceae | – | CABI (online) | |
Acacia nilotica | Fabaceae | Gum Arabic tree | CABI (online) | |
Acalypha | Euphorbiaceae | Copperleaf | CABI (online) | |
Acalypha indica | Euphorbiaceae | Indian copperleaf | García Morales et al. (2016) | |
Acanthus ilicifolius | Acanthaceae | – | CABI (online) | |
Albizia lebbeck | Fabaceae | Indian siris | CABI (online) | |
Alcea rosea | Malvaceae | Hollyhock | CABI (online) | |
Alhagi maurorum | Fabaceae | Camelthorn | CABI (online) | |
Annona | Annonaceae | – | CABI (online) | |
Annona muricata | Annonaceae | Soursop | CABI (online) | |
Annona reticulata | Annonaceae | Bullock's heart | CABI (online) | |
Annona squamosa | Annonaceae | Sugar apple | Fera, interception record, unpublished | |
Antigonon leptopus | Polygonaceae | Bride's tears | García Morales et al. (2016) | |
Apium graveolens | Apiaceae | Celery | García Morales et al. (2016) | |
Arachis hypogaea | Fabaceae | Groundnut | CABI (online) | |
Artocarpus altilis | Moraceae | – | García Morales et al. (2016) | |
Artocarpus heterophyllus | Moraceae | Jackfruit | CABI (online) | |
Artocarpus integer | Moraceae | Champedak | CABI (online) | |
Asparagus | Liliaceae | – | CABI (online) | |
Asparagus aethiopicus | Asparagaceae | Sprenger's asparagus | García Morales et al. (2016) | |
Asparagus densiflorus | Asparagaceae | Asparagus fern | García Morales et al. (2016) | |
Asparagus officinalis | Asparagaceae | Asparagus | CABI (online) | |
Averrhoa carambola | Oxalidaceae | Carambola | CABI (online) | |
Avicennia officinalis | Acanthaceae | – | García Morales et al. (2016) | |
Beaumontia | Apocynaceae | – | García Morales et al. (2016) | |
Beaumontia grandiflora | Apocynaceae | Easter lily vine | García Morales et al. (2016) | |
Breynia | Phyllanthaceae | – | CABI (online) | |
Breynia retusa | Phyllanthaceae | Cup–saucer plant | ||
Cactus | Cactaceae | – | García Morales et al. (2016) | |
Caesalpinia | Fabaceae | – | García Morales et al. (2016) | |
Cajanus | Fabaceae | – | CABI (online) | |
Cajanus cajan | Fabaceae | – | García Morales et al. (2016) | |
Callistemon | Myrtaceae | – | García Morales et al. (2016) | |
Camellia | Theaceae | – | García Morales et al. (2016) | |
Camellia sinensis | Theaceae | Tea | CABI (online) | |
Campsis grandiflora | Bignoniaceae | – | CABI (online) | |
Carica papaya | Caricaceae | Papaya | García Morales et al. (2016) | |
Cascaronia | Fabaceae | – | García Morales et al. (2016) | |
Casuarina | Casuarinaceae | Beefwood | CABI (online) | |
Casuarina equisetifolia | Casuarinaceae | Casuarina | CABI (online) | |
Catalpa | Bignoniaceae | – | García Morales et al. (2016) | |
Ceratonia | Fabaceae | – | García Morales et al. (2016) | |
Cestrum nocturnum | Solanaceae | Night jessamine | CABI (online) | |
Chrysanthemum | Asteraceae | – | García Morales et al. (2016) | |
Cicer arietinum | Fabaceae | Chickpea | CABI (online) | |
Citrus | Rutaceae | – | CABI (online) | |
Citrus aurantiifolia | Rutaceae | Lime | CABI (online) | |
Citrus aurantium | Rutaceae | Sour orange | CABI (online) | |
Citrus limon | Rutaceae | Lemon | CABI (online) | |
Citrus limonia | Rutaceae | Mandarin lime | CABI (online) | |
Citrus maxima | Rutaceae | Pummelo | CABI (online) | |
Citrus medica | Rutaceae | Citron | CABI (online) | |
Citrus reticulata | Rutaceae | Mandarin | CABI (online) | |
Citrus sinensis | Rutaceae | Sweet orange | CABI (online) | |
Citrus x paradisi | Rutaceae | Grapefruit | CABI (online) | |
Clausena lansium | Rutaceae | Wampee | García Morales et al. (2016) | |
Clerodendrum | Lamiaceae | – | García Morales et al. (2016) | |
Clerodendrum infortunatum | Lamiaceae | – | CABI (online) | |
Clerodendrum villosum | Lamiaceae | – | García Morales et al. (2016) | |
Cocos nucifera | Arecaceae | Coconut | CABI (online) | |
Coffea | Rubiaceae | Coffee | CABI (online) | |
Coffea arabica | Rubiaceae | Arabica coffee | CABI (online) | |
Coffea liberica | Rubiaceae | Liberian coffee tree | CABI (online) | |
Corchorus | Malvaceae | – | García Morales et al. (2016) | |
Corchorus capsularis | Tiliaceae | White jute | CABI (online) | |
Cucumis | Cucurbitaceae | – | García Morales et al. (2016) | |
Cucumis sativus | Cucurbitaceae | Cucumber | García Morales et al. (2016) | |
Cydonia oblonga | Rosaceae | Quince | García Morales et al. (2016) | |
Dalbergia | Fabaceae | – | García Morales et al. (2016) | |
Dalbergia sissoo | Fabaceae | Indian rosewood | García Morales et al. (2016) | |
Datura stramonium | Solanaceae | Jimsonweed | CABI (online) | |
Desmodium | Fabaceae | Tick clovers | CABI (online) | |
Dianthus caryophyllus | Caryophyllaceae | Carnation | García Morales et al. (2016) | |
Dimocarpus longan | Sapindaceae | Longan | García Morales et al. (2016) | |
Diospyros | Ebenaceae | – | García Morales et al. (2016) | |
Diospyros lotus | Ebenaceae | Caucasian persimmon | García Morales et al. (2016) | |
Eriobotrya japonica | Rosaceae | Loquat | CABI (online) | |
Erythrina variegata | Fabaceae | Indian coral tree | CABI (online) | |
Eugenia | Myrtaceae | – | García Morales et al. (2016) | |
Euphorbia | Euphorbiaceae | – | García Morales et al. (2016) | |
Euphorbia helioscopia | Euphorbiaceae | Sun spurge | García Morales et al. (2016) | |
Euphorbia hirta | Euphorbiaceae | Garden spurge | CABI (online) | |
Euphorbia prostrata | Euphorbiaceae | Blueweed | García Morales et al. (2016) | |
Falcataria falcata | Fabaceae | Batai wood | García Morales et al. (2016) | |
Ficus | Moraceae | – | CABI (online) | |
Ficus benghalensis | Moraceae | Banyan | CABI (online) | |
Ficus carica | Moraceae | Common fig | CABI (online) | |
Ficus sycomorus | Moraceae | Mulberry fig | García Morales et al. (2016) | |
Flacourtia | Salicaceae | – | García Morales et al. (2016) | |
Flacourtia indica | Salicaceae | Batoko plum | García Morales et al. (2016) | |
Flacourtia inermis | Salicaceae | Lovi–lovi | CABI (online) | |
Fritillaria | Liliaceae | |||
Gardenia jasminoides | Rubiaceae | Cape jasmine | CABI (online) | |
Geranium | Geraniaceae | – | García Morales et al. (2016) | |
Glochidion rubrum | Euphorbiaceae | – | CABI (online) | |
Glycine max | Fabaceae | Soyabean | CABI (online) | |
Glycosmis | Rutaceae | – | García Morales et al. (2016) | |
Glycosmis pentaphylla | Rutaceae | Gin berry | García Morales et al. (2016) | |
Gossypium | Malvaceae | Cotton | CABI (online) | |
Gossypium herbaceum | Malvaceae | Short staple cotton | CABI (online) | |
Gossypium hirsutum | Malvaceae | Bourbon cotton | CABI (online) | |
Grevillea robusta | Proteaceae | Silky oak | CABI (online) | |
Helianthus | Asteraceae | – | ||
Helianthus annuus | Asteraceae | Sunflower | García Morales et al. (2016) | |
Hibiscus | Malvaceae | Rosemallows | CABI (online) | |
Hibiscus manihot | Malvaceae | Bele | CABI (online) | |
Hibiscus syriacus | Malvaceae | Althaea | García Morales et al. (2016) | |
Holarrhena | Apocynaceae | – | García Morales et al. (2016) | |
Houttuynia | Saururaceae | – | Fera, interception record, unpublished | |
Hygrophila | Acanthaceae | – | García Morales et al. (2016) | |
Hygrophila auriculata | Acanthaceae | – | García Morales et al. (2016) | |
Hygrophila erecta | Acanthaceae | – | García Morales et al. (2016) | |
Hygrophila spinosa | CABI (online) | |||
Impatiens walleriana | Balsaminaceae | Busy‐lizzy | García Morales et al. (2016) | |
Intsia bijuga | Fabaceae | Bajam teak | García Morales et al. (2016) | |
Ipomoea | Convolvulaceae | – | García Morales et al. (2016) | |
Ixora | Rubiaceae | – | CABI (online) | |
Jacaranda mimosifolia | Bignoniaceae | Jacaranda | CABI (online) | |
Jatropha curcas | Euphorbiaceae | Jatropha | CABI (online) | |
Jatropha gossypifolia | Euphorbiaceae | – | García Morales et al. (2016) | |
Jatropha integerrima | Euphorbiaceae | – | García Morales et al. (2016) | |
Lagenaria siceraria | Cucurbitaceae | Bottle gourd | García Morales et al. (2016) | |
Lagerstroemia indica | Lythraceae | Cannonball | García Morales et al. (2016) | |
Lantana camara | Verbenaceae | Cherry pie | García Morales et al. (2016) | |
Leucaena | Fabaceae | CABI (online) | ||
Leucaena leucocephala | Fabaceae | Leucaena | CABI (online) | |
Leucas aspera | – | – | CABI (online) | |
Ligustrum | Oleaceae | – | García Morales et al. (2016) | |
Limonia | Rutaceae | – | García Morales et al. (2016) | |
Limonia acidissima | Rutaceae | Elephant apple | García Morales et al. (2016) | |
Luffa | Cucurbitaceae | – | García Morales et al. (2016) | |
Luffa aegyptiaca | Cucurbitaceae | Loofah | CABI (online) | |
Malus domestica | Rosaceae | Apple | García Morales et al. (2016) | |
Mangifera indica | Anacardiaceae | Mango | CABI (online) | |
Manihot esculenta | Euphorbiaceae | Cassava | García Morales et al. (2016) | |
Melochia | Malvaceae | – | García Morales et al. (2016) | |
Mimosa pudica | Fabaceae | Action plant | García Morales et al. (2016) | |
Morus | Moraceae | – | CABI (online) | |
Morus alba | Moraceae | Mora | CABI (online) | |
Morus nigra | Moraceae | Black mulberry | CABI (online) | |
Mucuna | Fabaceae | – | García Morales et al. (2016) | |
Murraya koenigii | Rutaceae | Curry leaf | García Morales et al. (2016) | |
Musa | Musaceae | – | García Morales et al. (2016) | |
Myrtus communis | Myrtaceae | Common myrtle | García Morales et al. (2016) | |
Nephelium lappaceum | Sapindaceae | Rambutan | García Morales et al. (2016) | |
Nerium indicum | Apocynaceae | Sweet oleander | García Morales et al. (2016) | |
Nerium oleander | Apocynaceae | Oleander | CABI (online) | |
Nyctanthes arbor‐tristis | Verbenaceae | Tree of sadness | CABI (online) | |
Ocimum tenuiflorum | Lamiaceae | Holy basil | CABI (online) | |
Odontadenia | Apocynaceae | – | CABI (online) | |
Olea europaea | Oleaceae | Common olive | García Morales et al. (2016) | |
Opuntia | Cactaceae | – | García Morales et al. (2016) | |
Parthenium hysterophorus | Asteraceae | Parthenium weed | CABI (online) | |
Pelargonium | Geraniaceae | – | García Morales et al. (2016) | |
Peristrophe bicalyculata | Acanthaceae | – | CABI (online) | |
Persea americana | Lauraceae | Avocado | CABI (online) | |
Phoenix dactylifera | Arecaceae | Common date palm | García Morales et al. (2016) | |
Phyllanthus emblica | Euphorbiaceae | Indian gooseberry | CABI (online) | |
Phyllanthus niruri | Euphorbiaceae | Seed‐under‐the‐leaf | CABI (online) | |
Pilea microphylla | Urticaceae | – | CABI (online) | |
Pilea serpyllacea | Urticaceae | – | García Morales et al. (2016) | |
Pinus | Pinaceae | Pines | CABI (online) | |
Pithecellobium | Fabaceae | – | García Morales et al. (2016) | |
Phyllanthus | Phyllanthaceae | – | García Morales et al. (2016) | |
Phyllanthus amarus | Phyllanthaceae | Black catnip | García Morales et al. (2016) | |
Phyllanthus emblica | Phyllanthaceae | Emblic | García Morales et al. (2016) | |
Plumeria rubra | Apocynaceae | Red frangipani | CABI (online) | |
Portulaca grandiflora | Portulacaceae | Rose moss | CABI (online) | |
Prosopis cineraria | Fabaceae | Khejri tree | García Morales et al. (2016) | |
Prosopis farcta | Fabaceae | Syrian mesquite | García Morales et al. (2016) | |
Prunus armeniaca | Rosaceae | Apricot | García Morales et al. (2016) | |
Psidium | Myrtaceae | – | García Morales et al. (2016) | |
Psidium guajava | Lithomyrtus | Guava | CABI (online) | |
Psophocarpus tetragonolobus | Fabaceae | Asparagus pea | García Morales et al. (2016) | |
Pterospermum acerifolium | Malvaceae | Dinner plate tree | CABI (online) | |
Punica granatum | Punicaceae | Pomegranate | CABI (online) | |
Pyrus communis | Rosaceae | Common pear | García Morales et al. (2016) | |
Ricinus communis | Euphorbiaceae | Castor‐oil plant | García Morales et al. (2016) | |
Robinia pseudoacacia | Fabaceae | Black locust | Ülgentürk et al. (2022) | |
Rosa | Rosaceae | – | García Morales et al. (2016) | |
Rosa canina | Rosaceae | Briar rose | García Morales et al. (2016) | |
Salvia splendens | Lamiaceae | Scarlet sage | García Morales et al. (2016) | |
Sanchezia nobilis | Acanthaceae | – | CABI (online) | |
Schefflera | Araliaceae | – | García Morales et al. (2016) | |
Schleinitzia fosbergii | Fabaceae | – | García Morales et al. (2016) | |
Serianthes nelsonii | Fabaceae | – | García Morales et al. (2016) | |
Sesbania sesban | Fabaceae | Egyptian rattlepod | García Morales et al. (2016) | |
Sida | Malvaceae | – | CABI (online) | |
Solanum | Solanaceae | – | García Morales et al. (2016) | |
Solanum lycopersicum | Solanaceae | Tomato | CABI (online) | |
Solanum melongena | Solanaceae | Eggplant | García Morales et al. (2016) | |
Solanum tuberosum | Solanaceae | Potato | CABI (online) | |
Sonchus | Asteraceae | – | García Morales et al. (2016) | |
Spathodea campanulata | Bignoniaceae | African tulip tree | CABI (online) | |
Streblus asper | Moraceae | Sandpaper tree | CABI (online) | |
Suregada | Euphorbiaceae | – | García Morales et al. (2016) | |
Suregada multiflora | Euphorbiaceae | – | García Morales et al. (2016) | |
Tabebuia rosea | Bignoniaceae | Rosy trumpet tree | García Morales et al. (2016) | |
Tagetes erecta | Asteraceae | African marigold | García Morales et al. (2016) | |
Tamarindus | Fabaceae | CABI (online) | ||
Tamarindus indica | Fabaceae | Tamarind | CABI (online) | |
Tamarix | Tamaricaceae | Tamarisk | CABI (online) | |
Tephrosia | Fabaceae | Hoary‐pea | CABI (online) | |
Thespesia | Malvaceae | – | García Morales et al. (2016) | |
Thespesia populnea | Malvaceae | Portia tree | CABI (online) | |
Tinospora cordifolia | Menispermaceae | – | ||
Trachelospermum | Apocynaceae | – | García Morales et al. (2016) | |
Trachelospermum lucidum | Apocynaceae | – | García Morales et al. (2016) | |
Vachellia nilotica | Fabaceae | Egyptian mimosa | García Morales et al. (2016) | |
Verbena | Verbenaceae | – | García Morales et al. (2016) | |
Vigna radiata | Fabaceae | Mung bean | CABI (online) | |
Vitex negundo | Lamiaceae | CABI (online) | ||
Vitis | Vitaceae | – | García Morales et al. (2016) | |
Vitis vinifera | Vitaceae | Grapevine | CABI (online) | |
Ziziphus | Rhamnaceae | CABI (online) | ||
Ziziphus jujuba | Rhamnaceae | Common jujube | CABI (online) | |
Ziziphus mauritiana | Rhamnaceae | Jujube | CABI (online) | |
Ziziphus spina‐christi | Rhamnaceae | Christ's thorn jujube | CABI (online) | |
Zygophyllum fabago | Zygophyllaceae | Bean caper | García Morales et al. (2016) | |
Wild weed hosts | Acacia karroo | Fabaceae | Sweet thorn | CABI (online) |
Clerodendrum villosum |
Lamiaceae | – | CABI (online) | |
Cuscuta exaltata | Convolvulaceae | Dodder | CABI (online) | |
Cynodon dactylon | Poaceae | Bahama grass | García Morales et al. (2016) | |
Solanum nigrum | Solanaceae | Black nightshade | García Morales et al. (2016) |
Appendix B – Distribution of Nipaecoccus viridis
Distribution records based on EPPO Global Database (EPPO, online), García Morales et al. (2016) and CABI (online).
Region | Country | Sub‐national (e.g. State) | Status | |
---|---|---|---|---|
North America | Bahamas | Present, no details | EPPO (online) | |
Mexico | Present, no details | EPPO (online) | ||
United States of America | Present, restricted distribution | EPPO (online) | ||
United States of America | Florida | Present, no details | EPPO (online) | |
United States of America | Hawaii | Present, no details | EPPO (online) | |
United States of America | Guam | Present, no details | García Morales et al. (2016) | |
Africa | Algeria | Present, no details | EPPO (online) | |
Angola | Present, no details | EPPO (online) | ||
Benin | Present, no details | EPPO (online) | ||
Burkina Faso | Present, no details | EPPO (online) | ||
Comoros | Present, no details | EPPO (online) | ||
Cote d'Ivoire | Present, no details | EPPO (online) | ||
Egypt | Present, no details | EPPO (online) | ||
Eritrea | Present, no details | EPPO (online) | ||
Kenya | Present, no details | EPPO (online) | ||
Madagascar | Present, no details | EPPO (online) | ||
Malawi | Present, no details | EPPO (online) | ||
Mali | Present, no details | EPPO (online) | ||
Mauritius | Present, no details | EPPO (online) | ||
Niger | Present, no details | EPPO (online) | ||
Nigeria | Present, no details | EPPO (online) | ||
Reunion | Present, no details | EPPO (online) | ||
Rwanda | Present, no details | EPPO (online) | ||
Senegal | Present, no details | EPPO (online) | ||
Seychelles | Present, no details | EPPO (online) | ||
South Africa | Present, no details | EPPO (online) | ||
Sudan | Present, no details | EPPO (online) | ||
Tanzania | Present, no details | EPPO (online) | ||
Togo | Present, no details | EPPO (online) | ||
Uganda | Present, no details | EPPO (online) | ||
Zambia | Present, no details | CABI (online) | ||
Zimbabwe | Present, no details | EPPO (online) | ||
Asia | Afghanistan | Present, no details | EPPO (online) | |
Bangladesh | Present, no details | EPPO (online) | ||
Bhutan | Present, no details | García Morales et al. (2016) | ||
Burma (=Myanmar) | Present, no details | García Morales et al. (2016) | ||
Cambodia | Present, no details | EPPO (online) | ||
China | Present, no details | EPPO (online) | ||
China | Hainan | Present, no details | García Morales et al. (2016) | |
China | Henan (=Honan) | Present, no details | García Morales et al. (2016) | |
China | Hunan | Present, no details | EPPO (online) | |
China | Xianggang (Hong Kong) | Present, no details | EPPO (online) | |
China | Nei Monggol (=Inner Mongolia) | Present, no details | García Morales et al. (2016) | |
India | Present, no details | EPPO (online) | ||
India | Assam | Present, no details | García Morales et al. (2016) | |
India | Andhra Pradesh | Present, no details | EPPO (online) | |
India | Bihar | Present, no details | EPPO (online) | |
India | Delhi | Present, no details | EPPO (online) | |
India | Goa | Present, no details | EPPO (online) | |
India | Gujarat | Present, no details | EPPO (online) | |
India | Himachal Pradesh | Present, no details | EPPO (online) | |
India | Karnataka | Present, no details | EPPO (online) | |
India | Kerala | Present, no details | EPPO (online) | |
India | Lakshadweep | Present, no details | CABI (online) | |
India | Madhya Pradesh | Present, no details | EPPO (online) | |
India | Maharashtra | Present, no details | EPPO (online) | |
India | Odisha | Present, no details | EPPO (online) | |
India | Punjab | Present, no details | EPPO (online) | |
India | Rajasthan | Present, no details | García Morales et al. (2016) | |
India | Tamil Nadu | Present, no details | EPPO (online) | |
India | Tripura | Present, no details | García Morales et al. (2016) | |
India | Uttar Pradesh | Present, no details | EPPO (online) | |
India | West Bengal | Present, no details | EPPO (online) | |
Indonesia | Present, no details | EPPO (online) | ||
Indonesia | Java | Present, no details | EPPO (online) | |
Indonesia | Irian Jaya | Present, no details | García Morales et al. (2016) | |
Indonesia | Sulawesi (=Celebes) | Present, no details | García Morales et al. (2016) | |
Iran | Present, no details | EPPO (online) | ||
Iraq | Present, no details | EPPO (online) | ||
Israel | Present, no details | EPPO (online) | ||
Japan | Present, no details | EPPO (online) | ||
Japan | Ryukyu Archipelago | Present, no details | EPPO (online) | |
Jordan | Present, no details | EPPO (online) | ||
Laos | Present, no details | García Morales et al. (2016) | ||
Malaysia | Present, no details | EPPO (online) | ||
Nepal | Present, no details | EPPO (online) | ||
Oman | Present, no details | EPPO (online) | ||
Pakistan | Present, no details | EPPO (online) | ||
Philippines | Present, no details | EPPO (online) | ||
Saudi Arabia | Present, no details | EPPO (online) | ||
Singapore | Present, no details | García Morales et al. (2016) | ||
Sri Lanka | Present, no details | EPPO (online) | ||
Syria | Present, no details | García Morales et al. (2016) | ||
Taiwan | Present, no details | EPPO (online) | ||
Thailand | Present, no details | EPPO (online) | ||
Vietnam | Present, no details | EPPO (online) | ||
Europe | Turkey | Present, restricted distribution | EPPO (online) | |
Oceania | Australia | Present, no details | EPPO (online) | |
Australia | Northern Territory | Present, no details | EPPO (online) | |
Australia | Queensland | Present, no details | EPPO (online) | |
Australia | Christmas island | Present, no details | García Morales et al. (2016) | |
Guam | Present, no details | EPPO (online) | ||
Kiribati | Present, no details | EPPO (online) | ||
New Caledonia | Present, widespread | EPPO (online) | ||
Northern Mariana Islands | Present, no details | EPPO (online) | ||
Papua New Guinea | Present, no details | EPPO (online) | ||
Solomon Islands | Present, no details | EPPO (online) | ||
Tuvalu | Present, no details | EPPO (online) | ||
United States of America | Guam | Present, no details | García Morales et al. (2016) |
Appendix C – Import data
Suggested citation: EFSA PLH Panel (EFSA Panel on Plant Health) , Bragard C, Baptista P, Chatzivassiliou E, Di Serio F, Gonthier P, Jaques Miret JA, Justesen AF, Magnusson CS, Milonas P, Navas‐Cortes JA, Parnell S, Potting R, Reignault PL, Stefani E, Thulke H‐H, Van der Werf W, Vicent Civera A, Yuen J, Zappalà L, Grégoire J‐C, Malumphy C, Kertesz V, Maiorano A and MacLeod A, 2023. Scientific Opinion on the pest categorisation of Nipaecoccus viridis . EFSA Journal 2023;21(1):7770, 44 pp. 10.2903/j.efsa.2023.7770
Requestor: European Commission
Question number: EFSA‐Q‐2022‐00761
Panel members: Claude Bragard, Paula Baptista, Elisavet Chatzivassiliou, Francesco Di Serio, Paolo Gonthier, Josep Anton Jaques Miret, Annemarie Fejer Justesen, Alan MacLeod, Christer Sven Magnusson, Panagiotis Milonas, Juan A Navas‐Cortes, Stephen Parnell, Roel Potting, Philippe L Reignault, Emilio Stefani, Hans‐Hermann Thulke, Wopke Van der Werf, Antonio Vicent Civera, Jonathan Yuen and Lucia Zappalà.
Declarations of interest: If you wish to access the declaration of interests of any expert contributing to an EFSA scientific assessment, please contact interestmanagement@efsa.europa.eu.
Acknowledgements: EFSA wishes to acknowledge the contribution of Oresteia Sfyra and Ana Guillem Amat to this opinion.
Adopted: 12 December 2022
Note
An EPPO code, formerly known as a Bayer code, is a unique identifier linked to the name of a plant or plant pest important in agriculture and plant protection. Codes are based on genus and species names. However, if a scientific name is changed the EPPO code remains the same. This provides a harmonized system to facilitate the management of plant and pest names in computerized databases, as well as data exchange between IT systems (Griessinger and Roy, 2015; EPPO, 2019).
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