Abstract:Following a request from the European Commission, the EFSA Panel on Plant Health performed a risk assessment of
Xanthomonas citri
pv.
viticola
(Xcv). This pest causes bacterial canker of grapevine and is reported from Brazil and India. Two scenarios were considered: scenario A0 (current practice) and A2 (additional control measures). For the fresh grape import pathway, scenario A0 results in an order of magnitude of about one entry per 10 years (median; 90% uncerta… Show more
“…In the assessment of potential spread, it is assumed that the founder population of R. citrifrugis occupies a limited proportion of available habitat (citrus plants or orchards located in a restricted area) with a small local population size (i.e. a fraction of the habitat's carrying capacity), in agreement with previous spread assessments (EFSA PLH Panel, 2022 ). Similarly, it is assumed that the initial increase in population size and the initial dispersal rate of R. citrifrugis are limited due to (a) (epi)‐genetic factors (lack of fitness of the species in a new environment) and (b) suboptimal environmental conditions reducing the fitness of the pest.…”
Section: Spreadmentioning
confidence: 78%
“…Note that one of the input parameters is a disaggregation of consignments factor (d) used to disaggregate the infested material entering into the EU to different locations in the risk assessment area, as in previous Panel PRAs (EFSA PLH Panel, 2017 , 2022 , 2023 ). For example, for d = 1, one ton of citrus fruit is delivered to one location, whereas if d = 2, one ton of citrus fruit is delivered to two locations (in consignments of 500 kg each).…”
Following a request from the European Commission, the EFSA Panel on Plant Health performed a risk assessment of the citrus fruit midge Resseliella citrifrugis (Diptera: Cecidomyiidae), an oligophagous species, which feeds on fruits of Citrus spp., and is reported from China. The pest was temporarily regulated in October 2022 (Regulation (EU) /1941 , under Art. 30 (2016 /2031). The entry risk assessment focused on the citrus fruit pathway. Three scenarios were considered: A0 (current practice, i.e. regulated pest for the EU), A1 (deregulation) and A2 (A0 with additional stand-alone post-harvest cold treatment). Based on the outputs of the entry model, under scenario A0, slightly less than 40 potential founder populations per year are expected (median; 90%-uncertainty interval between about one per 30 years and about 3,000 per year). Under scenario A1, the risk of entry increases by about three times and reaches about 120 potential founder populations per year (median; 90%-uncertainty interval between about one per 10 years and about 9,000 per year). Compared to scenario A0, the risk of entry is orders of magnitude lower for scenario A2 (median = about one potential founder population per 120 years; 90%-uncertainty interval between one per about 600 million years and about two per year). The main uncertainties in the entry assessment are the probability of transfer, the RRO effectiveness (for scenario A2) and the disaggregation of consignments (transport of citrus fruit in boxes or lots to different locations). For all scenarios, the number of established populations is only slightly lower than the number of potential founder populations. Establishment is thus not expected to be a major constraint for this pest to then spread and cause impacts, despite the uncertainty about the pest thermal requirements. The median lag period between establishment and spread is estimated to be about 18 months (90%-uncertainty interval between about 7 and 54 months). After the lag period, the median rate of spread by flying and due to transport of harvested citrus fruit from orchards to packinghouses is estimated at about 100 km/year (90%-range between about 40 and 500 km/year). The main uncertainties in the spread assessment include the level of susceptibility of cultivars of different citrus species in the EU, the spread rate in China and the climate suitability of the initial spread focus in the EU. The median impact of R. citrifrugis in the EU citrus-growing area (proportion of infested citrus fruit out of harvested citrus fruit) is estimated at about 10% (90%-uncertainty interval between about 2% and 25%). Uncertainties affecting the impact assessment include the susceptibility of different citrus cultivars and the effect of the citrus fruit-harvesting season in the EU (mainly winter, the less suitable season for the pest).
“…In the assessment of potential spread, it is assumed that the founder population of R. citrifrugis occupies a limited proportion of available habitat (citrus plants or orchards located in a restricted area) with a small local population size (i.e. a fraction of the habitat's carrying capacity), in agreement with previous spread assessments (EFSA PLH Panel, 2022 ). Similarly, it is assumed that the initial increase in population size and the initial dispersal rate of R. citrifrugis are limited due to (a) (epi)‐genetic factors (lack of fitness of the species in a new environment) and (b) suboptimal environmental conditions reducing the fitness of the pest.…”
Section: Spreadmentioning
confidence: 78%
“…Note that one of the input parameters is a disaggregation of consignments factor (d) used to disaggregate the infested material entering into the EU to different locations in the risk assessment area, as in previous Panel PRAs (EFSA PLH Panel, 2017 , 2022 , 2023 ). For example, for d = 1, one ton of citrus fruit is delivered to one location, whereas if d = 2, one ton of citrus fruit is delivered to two locations (in consignments of 500 kg each).…”
Following a request from the European Commission, the EFSA Panel on Plant Health performed a risk assessment of the citrus fruit midge Resseliella citrifrugis (Diptera: Cecidomyiidae), an oligophagous species, which feeds on fruits of Citrus spp., and is reported from China. The pest was temporarily regulated in October 2022 (Regulation (EU) /1941 , under Art. 30 (2016 /2031). The entry risk assessment focused on the citrus fruit pathway. Three scenarios were considered: A0 (current practice, i.e. regulated pest for the EU), A1 (deregulation) and A2 (A0 with additional stand-alone post-harvest cold treatment). Based on the outputs of the entry model, under scenario A0, slightly less than 40 potential founder populations per year are expected (median; 90%-uncertainty interval between about one per 30 years and about 3,000 per year). Under scenario A1, the risk of entry increases by about three times and reaches about 120 potential founder populations per year (median; 90%-uncertainty interval between about one per 10 years and about 9,000 per year). Compared to scenario A0, the risk of entry is orders of magnitude lower for scenario A2 (median = about one potential founder population per 120 years; 90%-uncertainty interval between one per about 600 million years and about two per year). The main uncertainties in the entry assessment are the probability of transfer, the RRO effectiveness (for scenario A2) and the disaggregation of consignments (transport of citrus fruit in boxes or lots to different locations). For all scenarios, the number of established populations is only slightly lower than the number of potential founder populations. Establishment is thus not expected to be a major constraint for this pest to then spread and cause impacts, despite the uncertainty about the pest thermal requirements. The median lag period between establishment and spread is estimated to be about 18 months (90%-uncertainty interval between about 7 and 54 months). After the lag period, the median rate of spread by flying and due to transport of harvested citrus fruit from orchards to packinghouses is estimated at about 100 km/year (90%-range between about 40 and 500 km/year). The main uncertainties in the spread assessment include the level of susceptibility of cultivars of different citrus species in the EU, the spread rate in China and the climate suitability of the initial spread focus in the EU. The median impact of R. citrifrugis in the EU citrus-growing area (proportion of infested citrus fruit out of harvested citrus fruit) is estimated at about 10% (90%-uncertainty interval between about 2% and 25%). Uncertainties affecting the impact assessment include the susceptibility of different citrus cultivars and the effect of the citrus fruit-harvesting season in the EU (mainly winter, the less suitable season for the pest).
“…In the assessment of potential spread, the Panel assumed that the founder population of C. sagittiferella occupies a limited proportion of available habitat (citrus plants or orchards located in a restricted area) with a small local population size (i.e. a fraction of the habitat's carrying capacity), consistently with previous spread assessments (EFSA PLH Panel et al, 2022). Similarly, it is assumed that the initial increase in population size and the initial dispersal rate of C. sagittiferella are limited due to: a) (epi)-genetic factors (lack of fitness of the species in a new environment), b) suboptimal environmental conditions reducing the fitness of the pest.…”
Following a request from the European Commission, the EFSA Panel on Plant Health performed a risk assessment of Citripestis sagittiferella (Lepidoptera: Pyralidae), the citrus pulp borer, an oligophagous pest reported from South-East Asia and restricted to Citrus spp. The entry risk assessment focused on the citrus fruit pathway. Two scenarios were considered: scenario A0 (current practice) and A2 (additional post-harvest cold treatment). Based on the outputs of the entry model obtained in scenario A0, the median number of founder populations in the EU citrus-growing area is estimated to be slightly less than 10 per year (90%-uncertainty interval between about one entry per 180 years and 1,300 entries per year). The risk of entry and the simulated numbers of founder populations are orders of magnitude lower for scenario A2 compared to scenario A0. The key uncertainties in the entry model include transfer, the cold treatment effectiveness, the disaggregation factor and sorting. The simulated numbers of established populations are only slightly lower than the numbers of founder populations. As the probability of establishment has little impact on the number of established populations, it is not a major source of uncertainty, despite the lack of data on the thermal biology of the pest. The median lag period between establishment and spread is estimated to be slightly more than 1 year (90%uncertainty interval between about 2 months and 33 months). After the lag period, the median spread rate by natural means (flying) and due to transport of harvested citrus fruit from orchards to packinghouses is estimated at about 100 km/year (90%-uncertainty interval between about 40 and 500 km/year). The main sources of uncertainties affecting the spread rate include the extent to which environmental factors could hamper the build-up of the populations and the lack of data on the spread rate at the origin. The median impact of C. sagittiferella in the EU citrus-growing area is estimated at about 10% of infested fruits among the harvested citrus fruits (90%-uncertainty interval between about 2% and 25%). Uncertainties affecting the impact assessment include the susceptibility of different Citrus species and cultivars.
“…The first quantitative pest risk assessment which included a climate change scenario informing establishment likelihood was published for the pathogen of grapevine Xanthomonas citri pv . viticola (EFSA PLH Panel, 2022). Factors such as the appearance of heavier storms owing to the tropicalization of climate around the Mediterranean and effects on host plants distribution and phenology were considered when evaluating climate change scenarios.…”
Section: How Is Climate Change Currently Incorporated Into Risk Asses...mentioning
The evaluation of the potential for newly arrived species to survive and the determination whether a founder population can become established and subsequently spread and cause negative impacts are crucial considerations when performing a pest risk assessment in plant health. Climate change has clear consequences concerning the potential range of pests, and their potential for spread and impacts. Despite its importance, no guidance exists to support the evaluation of whether and how climate change should be incorporated into pest risk assessment. This paper reviews how climate change has been considered so far, not only in the area of pest risk assessment but also in other domains and provides guidance on how its incorporation could affect the overall assessment. Furthermore, from this analysis, some possible solutions for incorporating climate change into pest risk assessment are provided, taking into account that its outcomes have profound political, economic, social and environmental implications.
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