Abstract
The EFSA Panel on Plant Health conducted a pest categorisation of chickpea chlorotic dwarf virus (CpCDV) for the EU territory. The identity of CpCDV, a member of the genus Mastrevirus (family Geminiviridae) is established. Reliable detection and identification methods are available. The pathogen is not included in the EU Commission Implementing Regulation 2019/2072. CpCDV has been reported in Africa, Asia and Oceania. It has not been reported in the EU. CpCDV infects plant species in the family Fabaceae and several species of other families (Amaranthaceae, Brassicaceae, Caricaceae, Cucurbitaceae, Malvaceae and Solanaceae), including weeds. It may induce symptoms on its hosts, causing severe yield reduction. The virus is transmitted in a persistent, circulative and non‐propagative manner by the leafhopper species Orosius orientalis and O. albicinctus, which are not regulated. O. orientalis is known to be present in some EU member states. Plants for planting (other than seeds), parts of plants and cut flowers of CpCDV hosts and viruliferous leafhoppers were identified as the most relevant pathways for the entry of CpCDV into the EU. Cultivated and wild hosts of CpCDV are distributed across the EU. Would the pest enter and establish in the EU territory, impact on the production of cultivated hosts is expected. Phytosanitary measures are available to prevent entry and spread of the virus in the EU. CpCDV fulfils the criteria that are within the remit of EFSA to assess for it to be regarded as a potential Union quarantine pest.
Keywords: pest risk, plant health, plant pest, quarantine, CpCDV, Mastrevirus, leafhopper transmission
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
Chickpea chlorotic dwarf virus is one of a number of pests identified from horizon scanning and 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 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 quarantine pest, risk reduction options will be identified.
2. Data and methodologies
2.1. Data
2.1.1. Literature search
A literature search on chickpea chlorotic dwarf virus 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 EPPO Global Database, 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 chickpea chlorotic dwarf virus 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 chickpea chlorotic dwarf virus, following guiding principles and steps presented in the EFSA guidance on quantitative pest risk assessment (EFSA PLH Panel et al., 2018), the EFSA guidance on the use of the weight of evidence approach in scientific assessments (EFSA Scientific Committee, 2017) and the International Standards for Phytosanitary Measures No. 11 (FAO, 2013).
The criteria to be considered when categorising a pest as a potential Union quarantine pest (QP) are 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. Whilst 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 chickpea chlorotic dwarf virus is well established. It has been shown to produce consistent symptoms and to be transmissible.
Chickpea chlorotic dwarf virus (CpCDV) is classified in the species Chickpea chlorotic dwarf virus belonging to the genus Mastrevirus (family Geminiviridae, order Geplafuvirales) (ictv.global/taxonomy).
The species includes several viruses, namely CpCDV/A, CpCDV/B, CpCDV/C, CpCDV/D, CpCDV/E (https://ictv.global/vmr) from different geographic origins (Africa, Asia, Australia; Muhire et al., 2013). Isolates previously referred to as Bean yellow dwarf virus (Liu et al., 1997; AM849096, DQ458791; Y11023) were assigned to the species Chickpea chlorotic dwarf virus (https://ictv.global/ictv/proposals/2012.019abP.A.v3.Mastrevirus-17sp,rem-2sp.pdf).
Geminated CpCDV particles (Horn et al., 1993) encapsidate a monopartite circular, single‐stranded (ss) DNA genome, ca. 2.6 kb in size. The virus genome encodes four proteins, two of which in the virus sense strand (V1 and V2) and two in the complementary strand (C1 and C2). ORF V1 encodes the capsid protein (CP, 26.6 kDa), forming two incomplete icosahedra 22x38 nm in size. Besides being the only structural protein, the CP is a multifunctional protein serving as nuclear shuttle protein and with regulatory functions on ssDNA and dsDNA accumulation. ORF V2 encodes the 10‐kDA cell‐to‐cell movement protein. V1 and V2 expression is regulated by differential transcript splicing. Transcript splicing also regulates the replication associated protein expression from ORFs C1/C2 on the complementary strand, obtaining proteins Rep and RepA. RepA regulates the transactivation of virion‐sense ORFs and contributes to establishing a cellular environment favourable to virus replication. Rep recruits the needed host factors and initiates rolling‐circle DNA replication. Two non‐coding regions, the large intergenic region (LIR) and the short intergenic region (SIR), are present, containing transcription initiation and termination sites (Kanakala and Kuria, 2018; Fiallo‐Olivé et al., 2021). About 270 complete genome sequences of CpCDV and ca. 80 partial gene sequences are publicly available in GenBank database.
The EPPO code 1 (Griessinger and Roy, 2015; EPPO, 2019) for this species is CPCDV0 (EPPO, online).
3.1.2. Biology of the pest
CpCDV infects mostly dicotyledonous plants and was shown to be associated with the stunt disease of chickpea. In natural chickpea infections, CpCDV induces stunting, leaf size reduction, phloem browning of the collar region, with leaf chlorosis or reddening symptoms depending on the chickpea variety (Horn et al., 1993). As other mastreviruses, CpCDV is transmitted by leafhoppers (family Cicadellidae, order Hemiptera) in a persistent, circulative and non‐propagative manner (Fiallo‐Olivé et al., 2021). Leafhopper development proceeds from eggs, through nymphs to adults on host plants. Leafhopper females lay eggs into tender plant tissue, from which nymphs emerge and develop through five instars before maturing into adults. The pupal stage is not present (Weintraub et al., 2019). Horn et al. (1993) identified the leafhopper Orosius orientalis as the vector of CpCDV in India. The insect can acquire CpCDV in less than 2 min and is able to transmit it in about 2 h. CpCDV persists in O. orientalis up to 21 days (Horn et al., 1994). Nymphs can transmit the virus, which is also retained through moulting, generating viruliferous adults (Horn et al., 1994). CpCDV was shown to be transmitted also by another member of the genus Orosius, O. albicinctus, in Syria (Kumari et al., 2004) and Pakistan (Akhtar et al., 2011). CpCDV was detected in O. orientalis (Horn et al., 1994) and O. albicinctus (Akhtar et al., 2011) by ELISA. In the past, O. orientalis (Matsumura) and O. albicinctus (Distant) were often considered as synonyms. However, a revision of the genus Orosius based on male genitalia and barcoding clearly established that they represent two separate species (Fletcher et al., 2017). In a study on the identification of potential CpCDV vectors, the leafhopper Amrasca biguttula tested positive to CpCDV; however, no transmission assay was reported to confirm the molecular data (Reddy et al., 2020, 2021); therefore, such leafhopper species is considered as a potential vector with uncertainty. In addition, the leafhopper Neolimnus aegyptiacus was mentioned as a vector (Hamed and Makkouk, 2002), but in the absence of experimental data supporting this statement, it is not further considered in the present pest categorisation. CpCDV infects a variety of weeds (see Appendix A), which can act as alternative hosts for virus overwintering (Plant Health Australia, 2014). No seed transmission was reported for CpCDV (Plant Health Australia, 2014). As other mastreviruses, CpCDV was not mechanically transmitted to a number of experimental hosts (Horn et al., 1993; Farzadfar et al., 2008). However, the virus was successfully graft transmitted and induced chlorotic symptoms in Datura stramonium and Nicotiana tabacum cv. Samsun, and leaf rolling in N. tabacum cv. White Burley, or did not cause symptoms in Solanum lycopersicum and Vicia faba (Farzadfar et al., 2008). Experimental transmission can be achieved by Agrobacterium‐mediated inoculation (Fiallo‐Olivé et al., 2021).
3.1.3. Host range/species affected
CpCDV has been originally reported in chickpea (Cicer arietinum L.) plants in India (Horn et al., 1993). Natural infections of this virus occur on a range of cultivated species belonging to the Fabaceae family and other cultivated plants in the Amaranthaceae (i.e. sugar beet and spinach), Brassicaceae (i.e. brown and black mustard), Caricaceae (i.e. papaya), Cucurbitaceae (i.e. cucumber, watermelon and squash), Malvaceae (e.g. cotton) and Solanaceae (i.e. pepper, tomato) families.
Other natural hosts may also exist. Noteworthy, wild weed species were also found to be infected by CpCDV. Due to the lack of mechanical transmission, the CpCDV host range is difficult to study in laboratory conditions. However, several additional species of the families Amaranthaceae (Beta vulgaris), Brassicaceae (Arabidopsis thaliana), Fabaceae (Vicia faba) and Solanaceae (Nicotiana benthamiana, Nicotiana glutinosa, Nicotiana tabacum, Solanum lycopersicum, Capsicum annuum and Datura stramonium) have been successfully infected by using the leafhoppers O. albicinctus and O. orientalis as vectors (Horn et al., 1994; Farzadfar et al., 2008; Akhtar et al., 2011). Virus transmission was also achieved by grafting (Farzadfar et al., 2008) or via agroinfiltration in chickpea, N. benthamiana, N. glutinosa, N. tabacum and S. lycopersicum (Kanakala et al., 2013a,b; Nahid et al., 2008; Radouane et al., 2021; Fiallo‐Olivé et al., 2021). A detailed list of natural and experimental hosts of CpCDV is reported in Appendix A.
3.1.4. Intraspecific diversity
Due to the error‐prone viral replication system and the subsequent selection of the fittest variants in a certain environment, viruses have the typical features of quasi‐species (Andino and Domingo, 2015). This means that, even in a single host, they accumulate as a cluster of closely related sequence variants slightly differing from each other. Therefore, a certain level of intraspecific diversity is expected for all viruses. This genetic variability may interfere with the efficiency of detection methods. When data on the virus genome sequence variability are limited, the reliability of detection methods is associated with uncertainty.
About 270 full genome sequences and additional dozens of partial sequences are available in GenBank, providing information about the genetic variability of CpCDV. By analysing 939 full genome sequences of members of the genus Mastrevirus available in GenBank, a 94% sequence identity strain demarcation threshold for mastreviruses was proposed, such that genome sequences sharing identity above the 94% threshold are to be considered as variants of the same virus strain (Muhire et al., 2013; https://ictv.global/vmr). Seventeen CpCDV variants are known so far (Kanakala and Kuria, 2018). All CpCDV variants cluster in the same clade (Kanakala and Kuria, 2018). Intraspecies recombination events occurred at high frequency and had a major role in the generation of new variants (Kraberger et al., 2015). These recombination events may result in the evolution of CpCDV as a pathogen of new hosts (Kraberger et al., 2015).
3.1.5. Detection and identification of the pest
Are detection and identification methods available for the pest?
Yes, detection and identification methods are available for chickpea chlorotic dwarf virus.
A range of diagnostic protocols have been developed to detect and/or identify CpCDV either in host plants or in vectors. These include serological methods such as DAS‐ELISA, dot‐blot ELISA and tissue‐blot immunoassays using specific antisera (Horn et al., 1996; Kumari et al., 2006; Farzadfar et al., 2008; Akhtar et al., 2011). Molecular diagnostic protocols based on PCR employ degenerated primers which amplify a large part of the genome of dicot‐infecting mastreviruses (ca. 1.4 kb), followed by the use of gene‐specific primers (Farzadfar et al., 2008; Kanakala et al., 2013b). Rolling circle amplification (RCA) method is also available. In particular, RCA associated with restriction fragment length polymorphism (RFLP) has been widely used for CpCDV detection and characterisation (Haible et al., 2006; Hadfield et al., 2012; Fiallo‐Olivé et al., 2017; Hamza et al., 2018). Kanakala et al. (2013b) used dot‐blot hybridisation with a radiolabelled probe to detect CpCDV from field plants and electron microscopy to visualise CpCDV geminate particles.
Specific primers were developed and used in multiplex PCR to detect CpCDV (Nahid et al., 2008). Next‐generation sequencing techniques were employed to demonstrate that CpCDV is the causal agent of the ‘hard fruit syndrome’ of watermelon (Zaagueri et al., 2017).
3.2. Pest distribution
3.2.1. Pest distribution outside the EU
To date, CpCDV has been reported in Africa, Asia and Oceania (see Figure 1). Details on CpCDV worldwide distribution are summarised in Appendix B.
Figure 1.

Global distribution of CpCDV
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, chickpea chlorotic dwarf virus has not been reported in the EU.
To date, CpCDV has not been reported in the EU.
3.3. Regulatory status
3.3.1. Commission implementing regulation 2019/2072
CpCDV is not listed in Annex II of Commission Implementing Regulation (EU) 2019/2072 and 2021/2285, implementing acts 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
Plants for planting (other than seeds) of some hosts (Solanaceae) of CpCDV are prohibited from entering the Union from certain third countries under Commission Implementing Regulation (EU) 2019/2072 (Table 2).
Table 2.
List of plants, plant products and other objects that are CpCDV 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 | |
| 18. |
Plants for planting of Solanaceae other than seeds and the plants covered by entries 15, 16 or 17 |
ex 0602 90 30 ex 0602 90 45 ex 0602 90 46 ex 0602 90 48 ex 0602 90 50 ex 0602 90 70 ex 0602 90 91 ex 0602 90 99 |
Third countries other than: Albania, Algeria, Andorra, Armenia, Azerbaijan, Belarus, Bosnia and Herzegovina, Canary Islands, Egypt, Faeroe Islands, Georgia, Iceland, Israel, Jordan, Lebanon, Libya, Liechtenstein, Moldova, Monaco, Montenegro, Morocco, North Macedonia, Norway, Russia (only the following parts: Central Federal District (Tsentralny federalny okrug), Northwestern Federal District (Severo‐Zapadny federalny okrug), Southern Federal District (Yuzhny federalny okrug), North Caucasian Federal District (Severo‐Kavkazsky federalny okrug) and Volga Federal District (Privolzhsky federalny okrug)), San Marino, Serbia, Switzerland, Syria, Tunisia, Turkey and Ukraine and the United Kingdom |
3.3.3. Legislation addressing the organisms that vector CpCDV (commission implementing regulation 2019/2072)
The known vectors of CpCDV, the leafhoppers Orosius albicinctus and O. orientalis, are not regulated under Commission Implementing Regulation (EU) 2019/2072. Amrasca biguttula, a potential additional vector of CpCDV, is not regulated under Commission Implementing Regulation (EU) 2019/2072.
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, CpCDV may enter the EU with plants for planting (other than seeds), plants, parts of plants, and cut flowers of its hosts and with viruliferous leafhoppers on CpCDV hosts and non‐hosts.
Comment on plants for planting as a pathway.
Host plants for planting (other than seeds) is an entry pathway of CpCDV in the EU.
Table 3 provides broad descriptions of potential pathways for the entry of CpCDV into the EU.
Table 3.
Potential pathways for CpCDV into the EU 27
| Pathways | Life stage | Relevant mitigations [e.g. prohibitions (Annex VI), special requirements (Annex VII) or phytosanitary certificates (Annex XI) within Implementing Regulation 2019/2072] |
|---|---|---|
| Description (e.g. host/intended use/source) | ||
| Plants for planting, other than seeds, of CpCDV hosts* | N/A | Import of plants for planting (other than seeds) of Solanaceae from most third countries, including some of the countries in which CpCDV has been reported, is prohibited (Annex VI, 18). Import of plants for planting (other than seeds) of Solanaceae from some third countries in which CpCDV has been reported (e.g. Egypt, Morocco, Tunisia and Turkey), is not prohibited (Table 2). Import of host plants for planting other than seeds of other botanical families is not prohibited. |
| Plants, parts of plants, and cut flowers of CpCDV hosts | N/A | Phytosanitary certificate is requested for (i) foliage, branches and other parts of tomato […] plants, without flowers or flower buds, from third countries other than Switzerland (Annex XI, part A, 3); (ii) Solanaceae cut flowers and flower buds, foliage, branches and other parts of plants, without flowers and flower buds, from Americas and Australia (Annex XI, part A, 3); (iv) Cucurbita spp. (Annex XI, part B). |
| Viruliferous leafhoppers Orosius albicinctus and O. orientalis | Nymphs and adults | No special requirements are listed for these vectors |
Appendix A lists the hosts of CpCDV.
Import in the EU of Solanaceae host plants for planting of CpCDV is prohibited only from some third countries where CpCDV is present (Regulation 2019/2072, Annex VI, 18). Plants for planting (other than seeds), plants, parts of plants and cut flowers of CpCDV hosts can be imported to the EU with a phytosanitary certificate. O. albicinctus and O. orientalis are not regulated in the EU.
Notifications of interceptions of harmful organisms began to be compiled in Europhyt in May 1994 and in TRACES in May 2020. As on 9 September 2022, there were no records of interception of CpCDV and of the two vectors (O. albicinctus and O. orientalis) in the Europhyt and TRACES databases.
3.4.2. Establishment
Is the pest able to become established in the EU territory?
Yes, the virus could potentially establish wherever the hosts and competent leafhopper vector are available in the EU and the broader establishment of the virus is only limited by the presence of competent leafhopper vector(s).
CpCDV could potentially establish wherever its hosts and vector(s) are available in the EU. Natural hosts of CpCDV, in particular members of the families Fabaceae, Solanaceae, Cucurbitaceae and Amaranthaceae, are largely cultivated in the EU. Leafhopper vectors play a major role in the epidemiology of viruses due to their ability to transmit them to weeds when the crops are not available and to spread the virus to other hosts, thus contributing to the establishment and spread of the virus after its entry (Trębicki et al., 2010). At least one of the leafhoppers able to transmit CpCDV (O. orientalis) and one of the weed hosts (Xanthium strumarium, see Appendix A) are present in EU (see Section 3.4.3).
3.4.2.1. EU distribution of main host plants
Details on production area of leguminous plants are provided in Table 4. Details on production area of some among the most cultivated host species in several EU MSs, such as peppers, spinach, tomatoes and sugar beet, are provided in Appendices C–F, respectively.
Table 4.
Leguminous plants harvested green [G2000] crop production area (cultivation/harvested/production) (1,000 ha). Eurostat database, date of extraction 30 August 2022
| MS/TIME | 2017 | 2018 | 2019 | 2020 | 2021 |
|---|---|---|---|---|---|
| Belgium | 3.79 | 4.9 | 4.8 | 5.58 | 7.2 p |
| Bulgaria | 96.55 | 106.57 | 106.39 | 100.03 | 99.56 |
| Czechia | 174.87 | 181.3 | 192.49 | 198.05 | 201.96 |
| Denmark | 1.9 | 0.80 | 0.80 | 0.9 | 0.7 |
| Germany | 274.50 | 283.30 | 306.10 | 331.30 | 337.70 |
| Estonia | 34.68 | 33.69 | 28.66 | 30.79 | 33.16 |
| Ireland | 0.83 | 1.14 | 1.11 | 1.1 | 1.03 |
| Greece | 34.85 | 30.66 | 44.52 | 25.62 | 23.8 |
| Spain | 424.16 | 445.96 | 454.98 | 445.45 | 433.82 p |
| France | 373.98 | 425.36 | 476.52 | 508.82 | 520.83 |
| Croatia | 46.49 | 44.58 | 51.4 | 47.36 | 42.9 |
| Italy | 1,186.44 | 1,207.85 | 1,232.08 | 1,241.52 | 1,227.29 |
| Cyprus | 2.56 | 2.96 | 2.35 | 3.00 p | 4.00 e |
| Latvia | 29.4 | 19.6 | 32. | 33.10 | 35.50 |
| Lithuania | 47.12 | 54.69 | 63.62 | 71.33 | 77.96 |
| Luxembourg | 1.07 | 0.92 | 0.89 | 0.97 | 1.03 |
| Hungary | 206.93 | 214.22 | 233.96 | 219.45 | 217.98 |
| Malta | 0. | 0. | 0. | 0. | 0. |
| Netherlands | 8.50 | 8.65 | 8.63 | 8.70 | 8.42 |
| Austria | 76.73 | 75.65 | 78.89 | 80.01 | 77.96 |
| Poland | 173.3 | 148.14 | 138.41 | 177.64 | 181.11 e |
| Portugal | 12.69 | 10.71 | 14.14 | 14.15 | 14.15 p |
| Romania | 667.6 | 685.73 | 669.78 | 663.41 | 655.32 |
| Slovenia | 10.16 | 9.63 | 8.52 | 7.71 | 8.04 |
| Slovakia | 73.68 | 75.53 | 75.66 | 74.18 | 75.46 |
| Finland | 2. | 2.3 | 1.9 | 1.8 | 1.3 |
| Sweden | 0.00 n | 5.18 e | 1.62 | 3.09 | 0.00 n |
MS: member states; :, not available; e, estimated; n, not significant; p, provisional.
3.4.2.2. Climatic conditions affecting establishment
Except for climatic conditions affecting CpCDV hosts and vectors, no eco‐climatic constraints exist for the virus itself.
3.4.3. Spread
Describe how the pest would be able to spread within the EU territory following establishment?
The virus can spread both by natural and human‐assisted means.
Comment on plants for planting as a mechanism of spread.
Plants for planting (other than seeds) is a means of spread for the virus.
Natural spread of CpCDV in the field occurs through leafhopper vectors, Orosius orientalis and Orosius albicinctus, among which O. orientalis is known to be present in the EU territory. Uncertainty on A. biguttula as an additional vector exists. The virus transmission is persistent, circulative and non‐propagative (Fiallo‐Olivé et al., 2021). The adults are winged and able of short flights and jumps, and can be spread by wind (Trębicki et al., 2010). According to CABI, O. orientalis and O. albicinctus, which in this case are considered as synonyms, are present in Egypt, India, Iran, Israel, Japan, Myanmar, South Korea, Taiwan, Turkey and Australia (CABI, 2022). O. albicinctus has not been reported from the EU. O. orientalis has been reported in Malta (D'Urso et al., 2019). Fauna Europaea (https://fauna-eu.org, accessed September 6, 2022) reports O. orientalis as present in Greece, Spain and Portugal (Antonatos et al., 2020; EFSA PLH Panel et al., 2020). Notwithstanding the synonymy issues regarding O. orientalis and O. albicinctus have been recently solved (Fletcher et al., 2017) clarifying that they are two different species, there is uncertainty on their respective geographical distribution due to their possible misidentification in the past.
Amrasca biguttula, for which transmission experiments have not been performed yet, is considered widespread in southern East Asia, and present in Ghana (Africa) and Christmas Island and Guam (Oceania).
Human activities (trade of plants for planting other than seeds, ornamental plants, parts of plants, cut flowers and grafting) may contribute to further spread of the virus and/or viruliferous leafhoppers to larger distances.
3.5. Impacts
Would the pests' introduction have an economic or environmental impact on the EU territory?
Yes, should the virus be introduced and able to establish in the EU, an economic impact is expected.
Chickpeas infected by CpCDV are severely stunted with shortening of internodes and phloem browning. Leaf colour changes differ depending on the variety: leaves of Kabuli type chickpeas mostly show yellow, whereas those of Desi type become red (Horn et al., 1993). In India, it has been reported that if plants are infected at early growth stages, the pod production is aborted, with a yield loss of 100%, whereas in the case infection occurs at the flowering stage, the yield loss is up to 75–100% (Horn et al., 1995). In Sudan, stunt incidence was documented on chickpea, ranging between 7–25% and 25–62% depending on the season (Hamed and Makkouk, 2002). In Iran, an incidence of 3.4% and 1.8% was reported in faba bean and lentil, respectively (Shahmohammadi et al., 2020). In India, CpCDV induced stunting along with leaf curling in hot pepper (Capsicum annuum) (Byun et al., 2014). Mild chlorosis and stunting symptoms were shown to be induced by CpCDV on sugar beet plants in Iran (Farzadfar et al., 2008). Beside stunting, Cucurbita pepo plants showed leaf curling and yellow mottling, and a reduced fruit production in Egypt (Fahmy et al., 2015). Stunting, leaf curling and chlorosis were described in French bean (Liu et al., 1997) and spinach, which also showed vein thickening (Hamza et al., 2018). In Tunisia, CpCDV caused the hard fruit syndrome of watermelon, consisting of fruit and seed deformation, hardness and discoloration of the flesh bearing whitish inserts, associated with a bad taste (Zaagueri et al., 2017). The incidence in the field varied up to 70%, depending on the year (Zaagueri et al., 2017). Severe symptoms consisting of leaf dwarfing, yellowing and curling were described in papaya and tomato (Ouattara et al., 2017). Based on these data, should the virus enter and establish in the EU, an impact is expected. However, there is uncertainty on the magnitude of this impact.
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?
Measures are available to prevent entry, establishment and spread of CpCDV on its hosts.
3.6.1. Identification of potential additional measures
Phytosanitary measures (prohibitions) are currently applied to some host plants for planting other than seeds (see Section 3.3.2).
Additional potential risk reduction options and supporting measures are shown in Sections 3.6.1.1 and 3.6.1.2.
3.6.1.1. Additional potential risk reduction options
Potential additional control measures are listed in Table 5.
Table 5.
Selected control measures (a full list is available in EFSA PLH Panel et al., 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 | Plants for planting (other than seeds), plants, parts of plants and cut flowers of CpCDV hosts must come from a country officially free from the virus or from a pest‐free area or from a pest‐free place of production. | Entry/Spread/Impact |
| Growing plants in isolation | Growing plants in glass or plastic or in insect‐proof greenhouses would impair the spread of the virus by leafhoppers. | Entry (reduce contamination/infestation)/Spread/Impact |
| Managed growing conditions | Growing crops in ventilated tunnels may significantly reduce the entrance of O. orientalis (Weintraub et al., 2008) | Entry (reduce contamination/infestation)/Spread/Impact |
| Crop rotation, associations and density, weed/volunteer control | Controlling or avoiding the presence of weeds potentially hosting CpCDV and/or its vector and crop rotation with non‐host species, would impair the spread and incidence of the virus | Establishment/Spread/Impact |
| Use of resistant and tolerant plant species/varieties | Partially CpCDV‐resistant chickpea cultivar has been reported (Hamed and Makkouk, 2002) | Establishment/Impact |
| Roguing and pruning | Removal of symptomatic plants would decrease the virus inoculum | Spread/Impact |
| Timing of planting and harvesting | Delay chickpea planting by 3–4 weeks and shortening the irrigation intervals have been reported to reduce the CpCDV incidence in Sudan (Hamed and Makkouk, 2002). | Impact |
| Biological control and behavioural manipulation | Potential biological control agents against O. albicinctus have been reported (Bindra and Singh, 1970). No biological control against O. orientalis is available (Plant Health Australia, 2014) | Spread/Impact |
| Chemical treatments on crops including reproductive material | Chemical control of CpCDV vectors may impair virus spread. | Entry/Spread/Establishment/Impact |
| Chemical treatments on consignments or during processing | Chemical control of CpCDV vectors on consignments or during processing may impair virus spread. | Entry/Spread |
| Post‐entry quarantine and other restrictions of movement in the importing country | Post‐entry quarantine of plants for planting (other than seeds), plants, plant parts and cut flowers of some hosts of CpCDV (e.g. ornamental host plants for research, breading or other experimental purposes) could potentially mitigate the risk of entry of CpCDV and its leafhopper vectors into the EU | Entry/Establishment/Spread |
3.6.1.2. Additional supporting measures
Potential additional supporting measures are listed in Table 6.
Table 6.
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 | 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. Inspections in the field to detect early virus symptoms may be effective in reducing the field inoculum and may contribute to improve the efficacy of roguing. |
Entry/Establishment/Spread |
| Laboratory testing | Serological and molecular methods are available and can be used in laboratory testing | 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. Sampling is considered necessary as part of other RROs. |
Entry/Spread |
| Phytosanitary certificate and plant passport | A phytosanitary certificate and plant passport would reduce virus entry and spread. | Entry/Spread |
| Certified and approved premises | The risk is reduced if plants for planting of CpCDV hosts are from virus‐free approved premises | Entry/Spread |
| Certification of reproductive material (voluntary/official) | The risk is reduced if plants for planting of CpCDV hosts are from virus‐free approved premises and are certified as pest‐free | Entry/Spread |
| Delimitation of Buffer zones | Delimitation of a buffer zone is an effective measure to prevent spread of the virus in the EU | Spread |
| Surveillance | Surveillance is an effective measure to define pest‐free areas or pest‐free places of production as well as to prevent further spread of the virus | Spread |
3.6.1.3. Biological or technical factors limiting the effectiveness of measures
CpCDV asymptomatic infections and infected plants showing symptoms similar to those induced by other viruses or abiotic factors may reduce the efficacy of inspections.
Infected weeds favouring establishment and spread are difficult to monitor.
The occurrence of one of the proven vectors of CpCDV (O. albicinctus) may reduce the efficacy of any measure taken in those EU MSs where this vector occurs.
3.7. Uncertainty
There is no key uncertainty that may cast doubt on the conclusion of the pest categorisation.
4. Conclusions
Chickpea chlorotic dwarf virus fulfils the criteria that are within the remit of EFSA to assess for it to be regarded as a potential Union quarantine pest. Table 7 provides a summary of the PLH Panel conclusions.
Table 7.
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 chickpea chlorotic dwarf virus (CpCDV) is clearly defined | None |
| Absence/presence of the pest in the EU (Section 3.2 ) | CpCDV is not present in the EU | None |
| Pest potential for entry, establishment and spread in the EU (Section 3.4 ) | CpCDV could enter in the EU with plants for planting (other than seeds), parts of plants and cut flowers of its hosts. Viruliferous vectors are additional entry pathways | None |
| Potential for consequences in the EU (Section 3.5 ) | Introduction and further spread of CpCDV could have negative impact on the EU yield and quality production of the cultivated hosts. | None |
| Available measures (Section 3.6 ) | Phytosanitary measures are currently in place banning the import of plants for planting of CpCDV hosts in the family Solanaceae. Request of phytosanitary certificate is in place for plants, parts of plants and cut flowers of CpCDV hosts. Additional control measures are available to further mitigate the risk of entry, establishment, spread and impact of CpCDV in the EU. | None |
| Conclusion (Section 4 ) | CpCDV fulfils the criteria that are within the remit of EFSA to assess for it to be regarded as a potential Union quarantine pest. | None |
| Aspects of assessment to focus on/scenarios to address in future if appropriate: | Additional information on the presence and distribution of leafhopper vectors and virus natural host range would improve knowledge on the virus epidemiology | |
Abbreviations
- EPPO
European and Mediterranean Plant Protection Organisation
- FAO
Food and Agriculture Organisation
- 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, 2018)
- Control (of a pest)
Suppression, containment or eradication of a pest population (FAO, 2018)
- 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, 2018)
- Eradication (of a pest)
Application of phytosanitary measures to eliminate a pest from an area (FAO, 2018)
- Establishment (of a pest)
Perpetuation, for the foreseeable future, of a pest within an area after entry (FAO, 2018)
- 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, 2018)
- Pathway
Any means that allows the entry or spread of a pest (FAO, 2018)
- 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, 2018)
- 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, 2018)
- 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 2018)
Appendix A – Chickpea chlorotic dwarf virus host plants/species affected
Source: WoS
| Host status | Host name | Plant family | Common name | Reference |
|---|---|---|---|---|
| Cultivated hosts | Cicer arietinum | Fabaceae | Chickpea | |
| Lens culinaris | Fabaceae | Lentil | Makkouk et al. (2002, 2003a) | |
| Phaseolus vulgaris | Fabaceae | Bean | Farzadfar et al. (2002) | |
| Vicia faba | Fabaceae | Fava bean | Makkouk et al. (2003b); Kraberger et al. (2015); Shahmohammadi et al. (2020) | |
| Pisum sativum | Fabaceae | Pea | Kraberger et al. (2013) | |
| Beta vulgaris | Amaranthaceae | Sugar beet | Farzadfar et al. (2002) | |
| Spinacia oleracea | Amaranthaceae | Spinach | Hamza et al. (2018) | |
| Brassica juncea | Brassicaceae | Brown mustard | Reddy et al. (2021) | |
| Brassica nigra | Brassicaceae | Black mustard | Reddy et al. (2021) | |
| Carica papaya | Caricaceae | Papaya | Fiallo‐Olivé et al. (2017); Ouattara et al. (2017) | |
| Citrullus lanatus | Cucurbitaceae | Watermelon | Zaagueri et al. (2017); Radouane et al. (2019) | |
| Cucumis sativus | Cucurbitaceae | Cucumber | Hameed et al. (2017) | |
| Cucurbita sp. | Cucurbitaceae | Squash | Fahmy et al. (2015) | |
| Abelmoschus esculentus | Malvaceae | Okra | Zia‐Ur‐Rehman et al. (2017) | |
| Gossypium arboretum | Malvaceae | Tree cotton | Hameed et al. (2019) | |
| Gossypium hirsutum | Malvaceae | Cotton | Manzoor et al. (2014); Hameed et al. (2017) | |
| Capsicum annuum | Solanaceae | Bell pepper | Akhtar et al. (2014) | |
| Solanum lycopersicum | Solanaceae | Tomato | Zia‐Ur‐Rehman et al. (2015) | |
| Wild weed hosts | Xanthium strumarium | Asteraceae | Rough cocklebur | Mubin et al. (2012) |
| Aeschynomene virginica | Fabaceae | Virginia jointvetch | Reddy et al. (2021) | |
| Cajanus cajan | Fabaceae | Pigeon pea | Kraberger et al. (2015) | |
| Sesbania bispinosa | Fabaceae | Spiny sesbania | Nahid et al. (2008) | |
| Heteropogan contartus | Poaceae | Tussock grass | Reddy et al. (2021) | |
| Artificial/experimental hosts | Beta vulgaris | Amaranthaceae | Sugar beet | Horn et al. (1993) |
| Arabidopsis thaliana | Brassicaceae | Mouse‐ear cress | Liu et al. (1997) | |
| Cicer arietinum | Fabaceae | Chickpea | Horn et al. (1993) | |
| Lens esculenta | Fabaceae | Lentil | Horn et al. (1993) | |
| Phaseolus vulgaris | Fabaceae | Bean | Horn et al. (1993) | |
| Pisum sativum | Fabaceae | Pea | Horn et al. (1993) | |
| Vicia faba | Fabaceae | Fava bean | Farzadfar et al. (2008) | |
| Nicotiana benthamiana | Solanaceae | Benthi | Horn et al. (1993); Liu et al. (1997); Kanakala et al. (2013a); Manzoor and Bibi (2016); Khalid et al. (2017); Zaagueri et al. (2017); Hamza et al. (2018); Shahmohammadi et al. (2020) | |
| Nicotiana glutinosa | Solanaceae | Tobacco | Horn et al. (1993); Kanakala et al. (2013a) | |
| Nicotiana tabacum | Solanaceae | Tobacco | Horn et al. (1993); Liu et al. (1997); Farzadfar et al. (2008); Kanakala et al. (2013a); Hameed et al. (2019) | |
| Solanum lycopersicum | Solanaceae | Tomato | Liu et al. (1997); Farzadfar et al. (2008); Khalid et al. (2017) | |
| Datura stramonium | Solanaceae | Jimsonweed | Horn et al. (1993); Liu et al. (1997); Farzadfar et al. (2008) |
Appendix B – Distribution of chickpea chlorotic dwarf virus
Distribution records based on CABI and other sources
| Region | Country | Status (CABI) | References |
|---|---|---|---|
| Africa | Burkina‐Faso | Ouattara et al. (2020) | |
| Egypt | Present | CABI and EPPO (2005); Fahmy et al. (2015) | |
| Eritrea | Present, no details | Kumari et al. (2008) | |
| Ethiopia | Present | CABI and EPPO (2005); Abraham et al. (2000) | |
| Kenya | Avedi et al. (2020) | ||
| Morocco | Radouane et al. (2019) | ||
| Nigeria | Present | Fiallo‐Olivé et al. (2017) | |
| South‐Africa | Liu et al. (1997); Halley‐Stott et al. (2007) | ||
| Sudan | Present | CABI and EPPO (2005); Hamed and Makkouk (2002) | |
| Tunisia | Present | Zaagueri et al. (2017) | |
| Asia | India | Present | Byun et al. (2014) |
| Iran | Present | Makkouk et al. (2002) | |
| Iraq | Present | El‐Muadhidi et al. (2001) | |
| Oman | Present | Akhtar et al. (2014) | |
| Pakistan | Present | Horn et al. (1996); Nahid et al. (2008) | |
| Syria | Present | Kumari et al. (2004) | |
| Turkey | Kraberger et al. (2013) | ||
| Yemen | Present | CABI | |
| Oceania | Australia | Thomas et al. (2010) |
Appendix C – Peppers (Capsicum spp.) [V3600] crop production area
Eurostat database (cultivation/harvested/production) (1,000 ha); date of extraction 30 August 2022
| MS/TIME | 2017 | 2018 | 2019 | 2020 | 2021 |
|---|---|---|---|---|---|
| Belgium | 0.10 | 0.09 | 0.10 | 0.10 | 0.11 p |
| Bulgaria | 3.35 | 2.95 | 3.22 | 2.72 | 2.99 |
| Czechia | 0.00 n | 0.42 | 0.27 | 0.29 | 0.31 |
| Denmark | 0.00 n | 0.00 n | 0.00 n | 0.00 n | 0.00 n |
| Germany | 0.09 | 0.11 | 0.11 | 0.11 | 0.12 |
| Estonia | 0.00 | 0.00 | 0.00 | 0.00 | 0.00 |
| Ireland | 0.00 n | 0.00 n | 0.00 n | 0.00 n | 0.00 n |
| Greece | 4.03 | 3.84 | 3.39 | 3.45 | 3.40 |
| Spain | 20.50 | 20.58 | 21.43 | 21.75 | 22.24 |
| France | 0.96 | 0.95 | 0.94 | 1.16 | 1.36 |
| Croatia | 1.02 | 1.02 | 0.56 | 0.68 | 0.80 |
| Italy | 10.32 | 10.52 | 10.28 | 10.01 | 9.67 |
| Cyprus | 0.03 | 0.04 | 0.03 | 0.04 p | 0.04 p |
| Latvia | 0.00 n | 0.00 n | 0.00 n | 0.00 n | 0.00 n |
| Lithuania | 0.00 n | 0.00 n | 0.00 n | 0.00 n | 0.00 n |
| Luxembourg | 0.00 n | 0.00 n | 0.00 n | 0.00 n | 0.00 n |
| Hungary | 2.57 | 1.91 | 1.85 | 1.57 | 1.65 e |
| Malta | 0.00 n | 0.00 n | 0.00 n | 0.00 n | 0.00 n |
| Netherlands | 1.32 | 1.31 | 1.50 | 1.53 | 1.63 |
| Austria | 0.18 | 0.16 | 0.16 | 0.16 | 0.17 |
| Poland | 3.63 | 3.71 | 3.70 | 3.20 | 5.90 |
| Portugal | 1.21 | 0.93 | 0.85 | 1.28 | 1.23 p |
| Romania | 9.71 | 9.96 | 10.78 | 9.26 | 10.37 |
| Slovenia | 0.16 | 0.16 | 0.20 | 0.22 | 0.19 |
| Slovakia | 0.31 | 0.27 | 0.22 | 0.17 | 0.18 |
| Finland | 0.01 | 0.01 | 0.01 | 0.01 | 0.01 |
| Sweden | 0.00 | 0.00 | 0.00 | 0.00 | 0.00 |
MS, member states; :, not available; e, estimated; n, not significant; p, provisional.
Appendix D – Spinach [V2500] crop production area
Eurostat database (cultivation/harvested/production) (1,000 ha); date of extraction 30 August 2022
| MS/TIME | 2017 | 2018 | 2019 | 2020 | 2021 |
|---|---|---|---|---|---|
| Belgium | 5.09 | 4.59 | 4.69 | 4.54 | 4.44 p |
| Bulgaria | 0.07 | 0.13 | 0.09 | 0.15 | 0.07 |
| Czechia | 0.00 n | 0.39 | 0.47 | 0.33 | 0.63 |
| Denmark | 0.05 | 0.26 | 0.37 | 0.27 | 0.21 |
| Germany | 3.85 | 3.48 | 3.46 | 3.97 | 4.32 |
| Estonia | 0.00 | 0.00 | 0.00 | 0.00 | 0.00 |
| Ireland | 0.28 d | 0.23 B | 0.23 | 0.23 | 0.23 e |
| Greece | 9.97 | 7.57 | 6.77 | 6.92 | 6.99 |
| Spain | 4.35 | 4.5 | 4.3 | 4.86 | 5.11 |
| France | 5.31 | 6.06 | 5.89 | 5.32 | 4.97 |
| Croatia | 0.00 n | 0.00 N | 0.00 n | 0.00 n | 0.00 n |
| Italy | 5.97 | 6.59 | 6.29 | 6.14 | 6.08 |
| Cyprus | 0.06 | 0.06 | 0.08 | 0.08 p | 0.08 p |
| Latvia | 0.00 n | 0.00 N | 0.00 n | 0.00 n | 0.00 n |
| Lithuania | 0.02 | 0.04 | 0.15 | 0.1 | 0.04 |
| Luxembourg | 0.00 | 0.00 | 0.00 | 0.00 | 0.00 |
| Hungary | 0.37 | 0.45 | 0.47 | 0.46 | 0.45 e |
| Malta | 0.00 n | 0.00 N | 0.00 n | 0.00 n | 0.00 n |
| Netherlands | 2.92 | 3.14 | 3.39 | 3.3 | 3.49 |
| Austria | 0.67 | 0.77 | 0.77 | 0.64 | 0.57 |
| Poland | 1.09 e | 1.03 E | 0.7 e | 0.5 | 0.5 |
| Portugal | 0.54 | 0.44 | 0.55 | 0.99 | 0.87 p |
| Romania | 0.12 | 0.12 | 0.13 | 0.11 | 0.09 |
| Slovenia | 0.03 | 0.03 | 0.03 | 0.04 | 0.03 |
| Slovakia | 0.17 | 0.09 | 0.17 | 0.17 | 0.1 |
| Finland | 0.02 | 0.01 | 0.04 | 0.07 | 0.08 |
| Sweden | 0.04 | 0.07 | 0.07 | 0.07 | 0.08 |
MS, member states; :, not available; b, break in time series; d, definition differs (see metadata); e, estimated; n, not significant; p, provisional.
Appendix E – Tomatoes [V3100] crop production area
Eurostat database (cultivation/harvested/production) (1,000 ha); date of extraction 30 August 2022
| MS/TIME | 2017 | 2018 | 2019 | 2020 | 2021 |
|---|---|---|---|---|---|
| Belgium | 0.52 | 0.55 | 0.57 | 0.62 | 0.62 p |
| Bulgaria | 5.01 | 4.52 | 5.15 | 3.09 | 3.07 |
| Czechia | 0.24 | 0.3 | 0.16 | 0.26 | 0.26 |
| Denmark | 0.03 | 0.03 | 0.03 | 0.03 | 0.03 |
| Germany | 0.37 | 0.4 | 0.39 | 0.38 | 0.4 |
| Estonia | 0.00 | 0.00 | 0.00 | 0.01 | 0.01 |
| Ireland | 0.01 | 0.01 | 0.01 | 0.01 | 0.01 e |
| Greece | 13.32 | 16.02 | 15.01 | 15.82 | 16.09 |
| Spain | 60.85 | 56.13 | 56.94 | 55.47 | 56.11 |
| France | 5.75 | 5.74 | 5.66 | 5.95 | 6.22 |
| Croatia | 0.45 | 0.49 | 0.32 | 0.4 | 0.29 |
| Italy | 99.75 | 97.09 | 99.02 | 99.78 | 102.06 |
| Cyprus | 0.26 | 0.29 | 0.28 | 0.26 p | 0.28 p |
| Latvia | 0.00 | 0.00 | 0.00 n | 0.00 n | 0.00 n |
| Lithuania | 0.55 | 0.57 | 0.56 | 0.68 | 0.72 |
| Luxembourg | 0.00 | 0.00 | 0.00 | 0.00 | 0.00 |
| Hungary | 2.19 | 2.5 | 2.41 | 1.82 | 1.92 e |
| Malta | 0.00 n | 0.00 n | 0.00 n | 0.00 n | 0.00 n |
| Netherlands | 1.79 | 1.79 | 1.8 | 1.87 | 1.85 |
| Austria | 0.18 | 0.2 | 0.2 | 0.2 | 0.2 |
| Poland | 12.64 | 13.11 | 13.5 | 8.4 | 8.7 |
| Portugal | 20.87 | 15.83 | 15.89 | 15.04 | 17.78 p |
| Romania | 22.21 | 22.97 | 23.78 | 17.47 | 17.35 |
| Slovenia | 0.20 | 0.19 | 0.22 | 0.26 | 0.21 |
| Slovakia | 0.60 | 0.59 | 0.48 | 0.22 | 0.24 |
| Finland | 0.11 | 0.1 | 0.09 | 0.1 | 0.09 |
| Sweden | 0.04 | 0.04 | 0.04 | 0.05 | 0.04 |
MS: member states; :, not available; e, estimated; n, not significant; p, provisional.
Appendix F – Sugar beet (excluding seed) [R2000] crop production area
Eurostat database (cultivation/harvested/production) (1,000 ha); date of extraction 30 August 2022
| MS/TIME | 2017 | 2018 | 2019 | 2020 | 2021 |
|---|---|---|---|---|---|
| Belgium | 62.47 | 62.7 | 57.61 | 56.75 | 55.2 p |
| Bulgaria | 0.00 | 0.00 | 0.00 | 0.00 | 0.00 |
| Czechia | 66.10 | 64.76 | 59.21 | 59.68 | 61.23 |
| Denmark | 34.40 | 34.30 | 29.00 | 33.20 | 33.20 |
| Germany | 406.70 | 413.90 | 408.70 | 386.00 | 390.70 |
| Estonia | 0.00 | 0.00 | 0.00 | 0.00 | 0.00 |
| Ireland | 0.00 | 0.00 | 0.00 | 0.00 | 0.00 |
| Greece | 6.50 | 1.43 | 1.61 | 1.74 | 1.41 |
| Spain | 36.67 | 35.3 | 30.18 | 27.62 | 29.55 p |
| France | 486.10 | 485.85 | 446.60 | 420.89 | 402.16 |
| Croatia | 19.53 | 14.07 | 11.58 | 10.46 | 10.2 |
| Italy | 37.97 | 34.41 | 29.97 | 27.27 | 30.14 |
| Cyprus | 0.00 | 0.00 | 0.00 | 0.00 | 0.00 |
| Latvia | 0.00 | 0.00 | 0.00 | 0.00 | 0.00 |
| Lithuania | 17.15 | 15.54 | 14.12 | 13.99 | 14.68 |
| Luxembourg | 0.00 | 0.00 | 0.00 | 0.00 | 0.00 |
| Hungary | 18.65 | 15.77 | 14.08 | 12.91 | 12.17 |
| Malta | 0.00 | 0.00 | 0.00 | 0.00 | 0.00 |
| Netherlands | 85.35 | 85.2 | 79.18 | 81.46 | 80.51 |
| Austria | 42.68 | 31.25 | 27.88 | 26.32 | 37.85 |
| Poland | 231.72 | 238.92 | 240.78 | 245.92 | 250.57 e |
| Portugal | 0.11 | 0.00 | 0.00 | 0.00 | 0.00 n |
| Romania | 28.20 | 25.72 | 22.73 | 21.33 | 19.44 |
| Slovenia | 0.00 n | 0.00 n | 0.18 | 0.11 | 0.13 |
| Slovakia | 22.38 | 21.91 | 21.72 | 21.08 | 21.8 |
| Finland | 11.80 | 9.80 | 10.50 | 11.00 | 11.30 |
| Sweden | 30.99 | 30.64 | 27.16 | 29.75 | 28.7 |
MS: member states; :, not available; e, estimated; n, not significant; p, provisional.
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, MacLeod A, Magnusson CS, Milonas P, Navas‐Cortes JA, Parnell S, Potting R, Stefani E, Thulke H‐H, Van der Werf W, Vincent Civera A, Yuen J, Zappalà L, Migheli Q, Vloutoglou I, Czwienczek E, Streissl F, Carluccio AV, Chiumenti M, Di Serio F, Rubino L and Reignault PL, 2022. Scientific Opinion on the pest categorisation of chickpea chlorotic dwarf virus. EFSA Journal 2022;20(11):7625, 26 pp. 10.2903/j.efsa.2022.7625
Requestor European Commission
Question number EFSA‐Q‐2022‐00312
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.
Competing interests In line with EFSA's policy on declaration of interest, Panel member Francesco Di Serio did not participate in the adoption of this scientific opinion.
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.
Adopted: 29 September 2021
Notes
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 harmonised system to facilitate the management of plant and pest names in computerised databases, as well as data exchange between IT systems (Griessinger and Roy, 2015; EPPO, 2019).
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