Sampling and Detection Strategies for the Pine Pitch Canker (PPC) Disease Pathogen Fusarium circinatum in Europe

Review Sampling and Detection Strategies for the Pine Pitch Canker (PPC) Disease Pathogen Fusarium circinatum in Europe Eeva J. Vainio 1,*, Diana Bezos 2, Helena Bragança 3, Michelle Cleary 4, Gerda Fourie 5, Margarita Georgieva 6, Luisa Ghelardini 7, Salla Hannunen 8, Renaud Ioos 9, Jorge Martín-García2,10 , Pablo Martínez-Álvarez 2, Martin Mullett 11,12 , Tomasz Oszako 13 , Irena Papazova-Anakieva 14, Barbara Piškur 15 , Carmen Romeralo 2,4 , Antonio V. Sanz-Ros 2,16 , Emma T. Steenkamp 5, Katherine Tubby 11, Michael J. Wingfield 5 and Julio J. Diez 2 1Natural Resources Institute Finland, Latokartanonkaari 9, 00790 Helsinki, Finland 2 Sustainable Forest Management Research Institute, University of Valladolid—INIA, Avenida de Madrid 44, 34004 Palencia, Spain 3Instituto Nacional de Investigação Agrária e Veterinária, I.P. Av da República, Quinta do Marquês, 2780-159 Oeiras, Portugal 4Southern Swedish Forest Research Centre, Swedish University of Agricultural Sciences, Sundsvägen 3, 230 53 Alnarp, Sweden 5Forestry and Agricultural Biotechnology Institute (FABI), University of Pretoria, Hatfield 0083, Pretoria, South Africa 6Department of Forest Entomology, Phytopathology and Game fauna, Forest Research Institute, Bulgarian Academy of Sciences, 132 “St. Kliment Ohridski” Blvd., 1756 Sofia, Bulgaria 7 Department of Agriculture, Food, Environment and Forestry (DAGRI), University of Florence, Piazzale delle Cascine 18, 50144 Firenze, Italy 8Finnish Food Authority, Mustialankatu 3, 00790 Helsinki, Finland 9ANSES Plant Health Laboratory, Unit of mycology. Domaine de Pixérécourt, Bât. E., 54220 Malzéville, France 10 Department of Biology, CESAM (Centre for Environmental and Marine Studies), University of Aveiro, Campus Universitario de Santiago, 3810-193 Aveiro, Portugal 11 Forest Research, Farnham, Surrey GU10 4LH, Great Britain, UK 12 Phytophthora Research Centre, Mendel University in Brno, Zemˇedˇelská3, 613 00 Brno, Czech Republic 13 Forest Protection Department, Institute of Forest Research, Braci Le´snej 3, 05-090 Sekocin Stary, Poland 14 Faculty of Forestry, University “Ss Cyril and Methodius”- Skopje, 16 Makedonska brigada br.1, MK-1000 Skopje, Republic of North Macedonia 15 Slovenian Forestry Institute, Department of Forest Protection, Veˇcna pot 2, SI—1000 Ljubljana, Slovenia 16 Calabazanos Forest Health Centre (Junta de Castilla y León), Polígono industrial de Villamuriel, S/N, Villamuriel de Cerrato, 34190 Palencia, Spain *Correspondence: [email protected] Received: 20 June 2019; Accepted: 17 August 2019; Published: 22 August 2019   Abstract: Fusarium circinatum Nirenberg & O’Donnel is listed among the species recommended for regulation as quarantine pests in Europe. Over 60 Pinus species are susceptible to the pathogen and it also causes disease on Douglas-fir (Pseudotsuga menziesii (Mirb.) Franco) and species in genera such as Picea and Larix. The European Food Safety Authority considers the probability of new introductions—via contaminated seeds, wood material, soil and growing substrates, natural means and human activities—into the EU very likely. Due to early detection, constant surveillance and control measures, F. circinatum outbreaks have officially been eradicated in Italy and France. However, the global spread of F. circinatum suggests that the pathogen will continue to be encountered in new environments in the future. Therefore, continuous surveillance of reproductive material, nurseries and plantations, prompt control measures and realistic contingency plans will be important in Europe and elsewhere to limit disease spread and the “bridgehead effect”, where new introductions of a Forests 2019,10, 723; doi:10.3390/f10090723 www.mdpi.com/journal/forests Forests 2019,10, 723 2 of 27 tree pathogen become increasingly likely as new environments are invaded, must be considered. Therefore, survey programs already implemented to limit the spread in Europe and that could be helpful for other EU countries are summarized in this review. These surveys include not only countries where pitch canker is present, such as Portugal and Spain, but also several other EU countries where F. circinatum is not present. Sampling protocols for seeds, seedlings, twigs, branches, shoots, soil samples, spore traps and insects from different studies are collated and compiled in this review. Likewise, methodology for morphological and molecular identification is herein presented. These include conventional PCR with a target-specific region located in the intergenic spacer region, as well as several real-time PCR protocols, with different levels of specificity and sensitivity. Finally, the global situation and future perspectives are addressed. Keywords: Gibberella circinata; quarantine species; damping-off; survey programs; morphological identification; molecular detection 1. Introduction Fusarium circinatum Nirenberg & O’Donnel is a serious pathogen which affects certain conifers, and is considered to be native to Mexico, the Caribbean (Haiti) and the southeastern USA. The pathogen has spread from its original distribution area, and has been introduced to South America (Brazil, Chile, Colombia and Uruguay) [ 1 – 4 ] South Africa [ 5 ], Asia (Japan and South Korea) [ 6 , 7 ] and Southern Europe [ 8 – 11 ]. The global distribution of F. circinatum is mostly limited to Mediterranean and subtropical climates, with some spread into temperate climates [ 12 , 13 ]. The fungus has been found in four European countries (France, Italy, Portugal and Spain), but has established in forests only in the Iberian Peninsula. The European and Mediterranean Plant Protection Organization (EPPO) lists F. circinatum among the locally present species recommended for regulation as quarantine pests (A2 list). F. circinatum induces resinous bleeding cankers on trunks and branches of trees, and is commonly referred to as pine pitch canker [ 14 , 15 ]. On seedlings, the pathogen causes damping off, as well as root disease characterized by the discoloration and disintegration of the root cortex. Over 60 Pinus species are susceptible to infection by F. circinatum. The most susceptible species is Monterey pine (Pinus radiata D. Don), originating from the coast of central California USA and Mexico, which has been planted extensively around the globe, including in northeastern Spain [ 16 – 18 ]. Additionally, F. circinatum has been reported to cause disease on Douglas-fir (Pseudotsuga menziesii (Mirb.) Franco) and species in genera such as Picea and Larix [18,19]. The European Food Safety Authority (EFSA) panel has conducted a risk assessment of F. circinatum for the EU territory [ 13 ], and considers the probability of new entry into the EU very likely. The entry pathways include contaminated seeds, wood material, plant material for decorative purposes, soil and growing substrates, natural means (wind, rain, insects and other animals carrying spores) and human activities (travel, vehicles). This risk is mitigated through strict regulations on the importation and movement of plants belonging to the genus Pinus and Douglas-fir (including seeds and cones), together with the need for them to be officially inspected (imported plants) and accompanied by phytosanitary documents. In addition, growing media and wood packaging material imports are also regulated. These regulations do not include other conifers, such as Norway spruce (Picea abies (L.) Karst.), which could act as a path of entry for the pathogen. Mart í n-Garc í a et al., 2018 [ 19 ], demonstrated that asymptomatic Norway spruce seedlings could host latent infections of F. circinatum, even 8.5 months after inoculation. Based on a preliminary pest risk assessment by the French Plant Protection Service [ 20 ] and the first report of F. circinatum in the EU [ 21 , 22 ], provisional emergency measures were adopted in 2007 to prevent F. circinatum introduction into and spread within the Community (Commission Decision 2007/433/EC). This legislation stipulated that Member States of the EU must conduct official annual surveys for F. circinatum on their territory and report the results annually to the Forests 2019,10, 723 3 of 27 European Commission. Any suspected occurrence or confirmed presence of pine pitch canker must be reported to the National Plant Protection Organization (NPPO) of the corresponding country (see https://www.eppo.int/ABOUT_EPPO/eppo_members). In the case of confirmed presence of F. circinatum, EU Member States will define demarcated areas (including the infected zone and a buffer zone at least 1 km beyond the infected zone) and take official measures to eradicate the pest and to monitor for its presence. Since 2015, through Regulation (EU) No 652/2014, the EU has co-financed survey programs for certain pests, including F. circinatum. From 14 December 2019, new plant health rules will be applicable in the EU requiring Member States to perform regular surveys for the presence of all quarantine pests, consisting of visual examinations and, if appropriate, collecting and testing samples, based on sound scientific and technical principles (Regulation (EU) 2016/2031 of the European Parliament of the Council of 26 October 2016 on protective measures against pests of plants) [ 23 ]. From 31 March 2019, F. circinatum is listed in Annex I/A2 of the Plant Health Directive 2000/29/EC. Sampling for F. circinatum is essential in order to prevent its local establishment, spread and movement into disease-free areas, which is influenced by abiotic factors such as forest management and environmental conditions, as well as biotic factors (for example fungal communities and bark beetles) [ 24 ]. However, there are no harmonized sampling protocols or even a consensus about the best sampling methods and approaches. This leaves areas where “suboptimal” sampling protocols are used open to disease incursion. In this paper, we collate survey programs used in different countries, climatic zones and disease histories. We also discuss recommendations for sampling and processing plant tissues for the detection of F. circinatum as recommended by EPPO and the International Plant Protection Convention (IPPC). The overall aim is thus to provide authorities and pathologists with the relevant knowledge regarding the available approaches for surveys of their forests, plantations and nurseries. 2. Survey Programs in Different Geographical Regions 2.1. European Countries with Existing or Eradicated F. circinatum Epidemics All four of the European countries where F. circinatum has been detected are situated in the Mediterranean climatic zone. However, the pathogen is considered successfully eradicated in Italy and France and is currently present only in the Iberian Peninsula (Portugal and Spain). In all these countries, sampling is conducted yearly in forests, nurseries and garden centers. Tables 1–4present survey data from several countries based on the annual reports submitted to the European Commission by the NPPOs that are represented either by the current authors or collaborators mentioned in the Acknowledgements section. Forests 2019,10, 723 4 of 27 Table 1. Sampling approaches in production sites (nurseries) for planting material. The data is based on the annual reports submitted to the European Commission by the NPPOs. Country and Years Number in the Member State (Total Hectares) Visually Surveyed Locations (Number/Hectares) Number of Laboratory Samples Taken Results for Visually Surveyed Locations +/− Results for Laboratory Analyses+/− In case of Positive Findings Size (ha) and Location of Demarcated Area (Infected Zone +Buffer Zone) * Spain, Castilla y Le ó n, 2009–2017 13–121 nurseries of forest reproductive material (Pinus and/or P. menziesii) per year (658 in total) 21–52 per year (304 in total) 106–822 seedlings per year (3499 in total), and 1–165 seed lots per year (371 in total) 1 without symptoms 3 positive/3496 negative Data not available Spain, Cantabria 2009–2017 1–3 nurseries of forest reproductive material (Pinus and P. menziesii) per year 1–3 nurseries per year (17 in total) 102 samples in total all negative 4 positive in total n.a. Portugal, 2009–2017 100–224 nurseries of forest reproductive material (Pinus and P. menziesii) per year (1593 in total) 64–209 nurseries of forest reproductive material (Pinus and P. menziesii) per year (1245 in total) 154–259 per year (1908 in total) 4–17 with symptoms per year (79 in total) 0–13 positive, 154–257 negative per year (in total 40 positive, 1869 negative) 500–6269 ha located in 1–3 different regions per year (25,935 ha in total) Italy, 2010–2017 509–966 nurseries and garden centers of forest and ornamental trees per year 309–481 nurseries and garden centers of forest and ornamental trees per year (3240 in total) 43–309 per year (1111 in total) all negative all negative n.a. France, 2013–2017 1650–2554 nurseries per year (8187 in total; some of them are inspected every year) 1062–1331 per year (4868 in total) 17–47 per year (0–9 plants, 14–47 seed lots; 152 in total) all negative one positive seedlot from USA in 2016; all other years negative n.a. Bulgaria, 2015–2016 109 registered nurseries/1583.58 ha (authorized to issue plant passports) 84–89 nurseries (plants for planting) 226–334 ha 3–9 all negative all negative n.a. Northern Macedonia, 2007–2017 25–26 nurseries (total 80 ha) of forest propagation material (Pinus spp. and P. menziesii)+5 ha of nurseries of ornamental shrubs and trees 25–26 nurseries; 50–52 checks per year (Pinus spp. 30,337,150 seedlings and P. menziesii 1,612,400 seedlings in total) 58–80 all negative all negative or n.a. n.a. Slovenia, 2007–2017 19–45 places of production of plants for planting (per year) 19–45 visually surveyed locations (per year) 0–10 (per year) all negative all negative n.a. Great Britain, 2007–2017 206–313 Nurseries registered to issue plant passports where plants were inspected 163–323 sites inspected each year 0–84 (per year) all negative all negative or n.a. n.a. Sweden, 2014–2017 98 registered nurseries for forest propagation material 26–90 nurseries of forest reproductive material + 100 garden centers 0 no occurrence detected in surveys; no further sampling n.a. n.a. Finland, 2007–2017 33–76 nurseries of forest propagation material (Pinus and P. menziesii)+ca. 400 ha of nurseries of ornamental shrubs and trees 0–21 nurseries of forest reproductive material (up to ca. 22 million plants) +9–77 nurseries of ornamental shrubs and trees 0–11 per year samples taken from up to 4 locations; all negative all negative or n.a. n.a. *As described in article 6 of the Commission Decision 2007/433/EC. n.a. =not applicable. Forests 2019,10, 723 5 of 27 Table 2. Sampling approaches in production sites for planting material—demarcated Pinus spp. and Douglas-fir (Pseudotsuga menziesii) forest sites based on article 1 of the Commission Decision 2007/433/EC (separate, demarcated part of forest where propagating material as seeds and cones were collected). The data is based on the annual reports submitted to the European Commission by the NPPOs. Country and Years Total Hectares/Number in the Member State Visually Surveyed Locations Hectares/Number Number of Laboratory Samples Taken Results for Visually Surveyed Locations +/− Results for Laboratory Analyses+/− In case of Positive Findings Size (Ha) and Location of Demarcated Area (Infected Zone +Buffer Zone) Spain, Castilla y Le ó n, 2009–2017 3–10 sites per year 50 sites per year (129 sites in total) 23–2329 samples per year (3560 in total) 1–8 sites with symptoms 11 positives (between 2009 and 2011) 2535.7 ha in total Spain, Cantabria, 2009–2017 data not available data not available data not available data not available data not available data not available Portugal, 2009–2017 183 sites; about 12,000 ha (per year) 161 sites; about 201,802 ha (per year) 1–30 per year (110 in total) 1–26 sites with symptoms per year (79 in total) 2 positive (2016); other years negative 600 ha located in 1 region (2016); other years n.a. Italy, 2010–2017 17,920–25,279 ha +0–4 sites (2011–2017) 68 sites (2010) per year 27–1693 +0–4 sites (2011–2017) 41 sites (2010) per year (total 5120 ha +53 sites) 0–46 per year (108 in total) all negative all negative n.a. France, 2013–2017 21,894 ha per year (109,470 ha in total) included in forest survey see nurseries and forests see nurseries and forests see nurseries and forests see nurseries and forests Bulgaria, 2015–2016 3134.52 ha Pinus spp. and P. menziesii forestry stand and seed orchard 6.05–6.50 ha 0–11 (seed samples) negative all negative not applicable Northern Macedonia, 2007–2017 not available Pinus spp. 3 ha and P. menziesii 0.5 ha 0 n.a. all negative n.a. Slovenia, 2007–2017 not available included in forest surveys included in forest surveys all negative all negative n.a. Great Britain, 2007–2017 n.a. n.a. n.a. n.a. n.a. n.a. Sweden, 2014–2017 for Pinus spp. a 628 ha forestry stand and 1080 ha seed orchard; and for P. menziesii a 2 ha forestry stand 0 n.a. n.a. n.a. n.a. Finland, 2007–2017 1782–2434.2 ha (2007–2010); 0 ha (2011–2018) 0 10 places, 500 seed/place (2008); 0 (other years) n.a. all negative n.a. n.a. =not applicable. Forests 2019,10, 723 6 of 27 Table 3. Sampling approaches in Pinus spp. and Pseudotsuga menziesii forest (including parks, gardens etc.). The data is based on the annual reports submitted to the European Commission by the NPPOs. Country and Years Total Hectares/Number in Your Member State Visually Surveyed Locations Hectares/Number Number of Laboratory Samples Taken Results for Visually Surveyed Locations +/− Results for Laboratory Analyses+/− In case of Positive Findiings Size (ha) and Location of Demarcated Area (Infected Zone +Buffer Zone) Spain, Castilla y Le ó n, 2009–2017 1,291,800 ha per year (11,626,200 in total) 341–5738 sites per year (21,840 in total) 42–212 per year (1222 in total) 5–45 sites with symptoms per year (166 in total) 5 positive (2009–2013) data not available Spain, Cantabria, 2009–2017 12,213–33,129 ha 1160–2694 ha per year (12,446 ha in total) 34 in total 53 sites with symptoms 5 positive in total 10,666 ha in 16 demarcated areas since the detection of the pathogen in 2005 Portugal, 2009–2017 794,500–1,015,000 ha per year (8487,616 in total) 677–11,125 sites per year (46,696 in total) 4–77 per year (315 in total) 2–66 sites with symptoms per year (281 in total) 1 positive (2016); other years negative 550 ha located in 1 region (2016); other years n.a. Italy, 2010–2017 614,000–793,894 ha per year 1799–42,294 ha +719–12 sites per year (164,184 ha + 1596 sites in total) 30–160 (714 in total) all negative all negative n.a. France, 2013–2017 3,079,000 ha 48-111 forest sites inspected yearly; 104–191 inspections in parks and gardens yearly (939 sites in total) 3–17 per year 0 0 n.a. Bulgaria, 2015–2016 240,638 ha productive forests covered by Pinus spp. 7372 ha of P. menziesii plantations. it is also present in mixed forests, parks, gardens etc. in 263.01–386.30 ha forests covered by Pinus spp. 8–394.55 ha plantations covered by P. menziesii 0–6 all negative all negative not applicable Northern Macedonia, 2007–2017 80,000 ha 20,000 ha (surveyed area) Pinus spp.: 26 locations and P. menziesii: 3 locations 0 n.a. n.a. n.a. Slovenia, 2007–2017 cca. 80,000 ha of Pinus spp. and Pseudotsuga stands (around 6% of total wood stock) 98–900 ha (surveyed area); 28–7781 locations 0–55 all negative all negative n.a. Great Britain, 2007–2017 104 ha (P. radiata only); 416,424–448,284 ha 19–77 sites each year; 40.4–104.257 ha each year 0–88 (per year) all negative all negative or n.a. n.a. Sweden, 2014–2017 >9.2 million ha productive forests where at least 70% of the area is covered by Pinus spp. 0 0 n.a. n.a. n.a. Finland, 2007–2017 17,000,000 ha 0 0 n.a. n.a. n.a. n.a. =not applicable. Forests 2019,10, 723 7 of 27 Table 4. Sampling approaches in garden centers. The data is based on the annual reports submitted to the European Commission by the NPPOs. Country and Years Number of Inspections in Garden Centers Number of Laboratory Samples Taken Results for Laboratory Analyses+/− Spain, Castilla y León, 2009–2017 data not available data not available data not available Spain, Cantabria, 2009–2017 data not available data not available data not available Portugal, 2009–2017 data not available data not available data not available Italy, 2010–2017 included in production sites for planting material—nurseries included in production sites for planting material—nurseries included in production sites for planting material - nurseries France, 2013–2017 616 37 0 Bulgaria, 2015–2016 data not available data not available data not available Northern Macedonia, 2007–2017 included in forest survey included in forest survey included in forest survey Slovenia, 2007–2017 from 6 to 32 0–23 (per year; some samples taken from plants for planting, originating from other Member States) n.a. or negative Great Britain, 2007–2017 71–308 included in production sites for planting material—nursery surveys all negative or n.a. Sweden, 2014–2017 included in production sites for planting material—nurseries 0 n.a. Finland, 2007–2017 0–186 0 n.a. n.a. =not applicable. Forests 2019,10, 723 8 of 27 In Spain, the survey programs used in nurseries and forests vary across the seventeen Autonomous Communities. In Tables 1–4, sampling data are presented separately from two such regions with ongoing F. circinatum epidemics. As an example, in Castilla y Le ó n, forest nurseries and garden centers (all those growing susceptible species) are sampled annually by taking at least one sample per 20,000 plants in large nurseries (i.e., those producing millions of plants); the sampling frequency is higher for smaller nurseries. It is compulsory for the nurseries to declare their entire stock of plant material (including seed lots and the traceability of all plant material), which is taken into consideration when determining the minimum number of samples. Samples are taken preferably from symptomatic plants, but in the absence of symptoms, asymptomatic plants are also sampled. All nurseries that store seed lots are sampled every year, taking 500 seeds per seed lot (The Government of Spain; Real Decreto 637/2006 and 65/2010). Annual surveys of forests are carried out, with areas of susceptible tree species first being located and mapped. For example, in the Castilla y Le ó n region, besides the ICP Forests network (8 × 8 km grid and 4 × 4 km grid in protected areas), a specific 2 × 2 km grid has been established for F. circinatum in all Monterey pine plantations, also including surrounding maritime pine (P. pinaster Aiton) areas. In addition, the presence of F. circinatum symptoms is recorded in all stands monitored for the pine wood nematode (PWN; Bursaphelenchus xylophilus (Steiner & Buhrer) Nickle) (3000–5000 stands per year), and samples are taken for analysis when symptoms are observed. Moreover, nearly 800 environmental agents working in forests conducting different tasks (such as hunting, fishing, wood harvesting, etc.) monitor F. circinatum disease symptoms and collect samples from suspect plants. In contrast, in the Navarra region, besides three different grids (16 × 16 km, 8×8 km and 2 × 2 for the demarcated areas), roadsides and wood industries are also surveyed, taking advantage of ongoing PWN monitoring and the presence of seed orchards. In Portugal, all nurseries planting susceptible host species (including forest nurseries) must be inspected once a year by the phytosanitary inspection service before trade commences. If symptoms of F. circinatum are observed, samples are taken preferably from symptomatic plants according EPPO guidelines (https://gd.eppo.int/taxon/GIBBCI/documents). The following sampling scheme is used: 25 plants are collected from lots with <1000 seedlings, and 60 plants from lots with ≥ 1000 seedlings. The same number of asymptomatic plants is collected randomly if no symptoms are visible. Forest surveys are based on visual inspection of trees at field points classified as “coniferous forest cover” (>2170 points with an area of at least 500 m 2 each) from a 2 × 2 km grid developed by the Portuguese Forest Inventory (NFI). The grid is shifted annually, with reference to one of the four cardinal points, to maximize the detection of pests and pathogens [ 25 ]. Samples are taken only from plants that show symptoms characteristic of F. circinatum, focusing on: (i) areas surveyed for PWN (in the 20 km buffer-zone with the Spanish border); (ii) at least 25% of the forest points from the remaining territory, (iii) within 5 km around all commercial nurseries producing forest and ornamental conifer trees; (iv) in the 500 × 500 m zones in the demarcated areas established around nurseries and/or forest traders which had positive results for F. circinatum; and (v) in orchards (forest areas for seed production) inspected every three years and before collecting cones. All seed lots are analyzed before trade: a subsample of 500–1000 seeds per lot is subjected to laboratory analysis, and graft material of stone pine is also analyzed before trade. In Italy, surveillance activities are carried out independently by each Regional unit of the Phytosanitary Services on the basis of a coordinated National Surveillance Plan, which is updated yearly by the National Phytosanitary Committee (D.Lgs 214/05). Surveys are prescribed in four site types where host species of F. circinatum (all Pinus species and Douglas-fir) are found: (i) plant nurseries and commercial gardens; (ii) forests; (iii) forest areas for seed production; and (iv) green recreation areas including urban forests, parks and city gardens. Each surveillance site is permanent and corresponds to a circular area of about 30 m radius around a Global Positioning System (GPS) point where a visual inspection of symptoms on aerial plant parts is performed. Each inspected hectare should include 3 points. Plants with clear symptoms of infection are sampled for laboratory analysis. In addition, a minimum number of asymptomatic samples (i.e., 2 samples from at least 15% of the inspected sites) Forests 2019,10, 723 9 of 27 is currently recommended to be sent for molecular analyses (real-time PCR) both in forests and in forests for seed production. Twigs, branches or entire seedlings are usually sampled, while cones are collected at asymptomatic forest sites if crowns are not easily reached. Soil is not routinely sampled. There is considerable variation in the intensity and detail of planned surveillance among Italian regions depending on risk evaluation (climatic conditions, type, structure and age of forests, and the volume of local plant trade) [ 26 , 27 ]. With regard to forests and forest areas for seed production, Italian Regional Phytosanitary Services have reported their surveillance activities according to either inspected area (ha) or number of inspected sites, which makes it difficult to compare data among regions and to get a consistent picture at the national level. Instead, surveillance in nurseries is reported only as the number of inspected sites. From 2010 to 2017 in Italy about 54% (ca. 400 nurseries) of plant nurseries and commercial gardens growing F. circinatum host tree species were inspected yearly on average, with small differences from one year to another. In the same period, about 3% (ca. 21,000 ha) of Italian forests (aggregated data with green recreation areas) containing F. circinatum host species and about 2% (ca. 700 ha) of the area covered by demarcated forests for seed production, which are present in only a few regions, were inspected yearly on average. Data indicate year-to-year variation of the forest area inspected with a clear reduction after 2014, while the number of inspected nurseries remained quite stable. Since 2010, the number of samples collected for lab analyses has increased both in forests and in nurseries. In France, all nurseries with susceptible host species must be inspected once a year by the phytosanitary inspection services before trade commences. Only symptomatic plants and plant parts are sampled and sent for laboratory analysis using isolation techniques, followed by barcode sequence analysis of the fungus in pure culture. Forest sites are surveyed based on visual inspection, and samples are taken only from plants that show symptoms compatible with F. circinatum. The surveys emphasize high risk regions, e.g., those that are close to the Spanish border and/or show favorable climatic conditions (coastal areas of Languedoc Roussillon, Basque country, Landes, coastal areas of Charente-Maritime). Surveys are undertaken in parks and private gardens, forests and forest plantations (a minimum of 125 inspection visits in parks and 125 visits in forests per annum). Selected forest areas for seed production must be inspected every year before cone collection, during the same year when the harvest of seeds is scheduled. Moreover, all seed lots are analyzed before trade: a sub-sample of 1000 seeds per lot is taken and sent for laboratory analysis by real-time PCR. 2.2. European Countries without F. circinatum Outbreaks In European countries with temperate or boreal climatic conditions, the occurrence of symptoms compatible with F. circinatum is investigated in forests, nurseries and garden centers, as well as in gardens and parks in urban areas, and random samples are also sometimes taken from asymptomatic plants. Tables 1–4present survey data based on the annual reports submitted to the European Commission by the NPPOs for six exemplar countries: Bulgaria, North Macedonia and Slovenia represent mostly humid continental climatic zones, Great Britain represents the Oceanic climate zone and Sweden and Finland represent Nordic countries mostly located in the boreal forest zone. In Bulgaria, the diverse continental-Mediterranean climatic conditions and landscape patterns are considered likely to be favorable for the establishment F. circinatum [13]. The total area of established Pinus stands in forests and urban zones is 240,638 ha, and the current area of Douglas-fir plantations totals about 7372 ha. A survey to ascertain the presence of F. circinatum is carried out annually by phytosanitary inspectors from the Bulgarian Food Safety Agency (BFSA) at the Ministry of Agriculture and Food (2007–2017). Samples are only taken of symptomatic plants and are sent to the Central Laboratory of Quarantine Plants at BFSA. During 2015–2016, the number of nurseries in which Pinus and Douglas-fir were investigated was 84–89, and 394–658 hectares of forests and urban areas were also examined. In addition to these surveys, phytopathologists from the Forest Research Institute – BAS and Forest Protection Stations implement annual monitoring in order to assess the health status of stands and plantations of Scots pine (Pinus sylvestris L.), Austrian pine (P. nigra Arnold), Monterey pine and Douglas-fir. Forests 2019,10, 723 16 of 27 and this number may be determined as described by the IPPC (ISPM No. 31) [ 61 ]. Accordingly, there is also no standard protocol on how to process seed in the laboratory. In Spain, however, half of each sample (i.e., 250 seeds) is incubated on PDAS medium and the other half on Komada’s medium (Table 5) (The Government of Spain; Real Decreto 637/2006). Methods based on in vitro cultures focus mainly on the detection of F. circinatum externally. However, a preliminary biological enrichment step can be conducted prior to molecular detection of the pathogen by conventional or real-time PCR analysis in order to enhance the sensitivity of the detection for low levels of infection [47]. In certain cases, a seed lot can be composed of millions of seeds, and stored in several containers. In these cases, seeds should be sampled representatively; thus, one sample should contain seeds from each container and from different depths. In general, rules for seed testing are described by ISTA [ 62 ]. Occasionally, the percentage of infection in the lot is very low (1–5 seeds per 500), making analyses difficult and the introduction of the fungus due to detection failure more likely. 5.4. Soil Samples In the laboratory, the collected samples of rhizosphere soil are air-dried in a laminar flow hood for 24 to 48 h, and then ground in order to generate soil particles of a consistent size for use in soil dilutions; finally, they are plated onto a growth medium [ 31 ]. Alternatively, the method described by Hernandez-Escribano et al. [ 38 ] can be used for detecting the presence of F. circinatum in the collected soil. Briefly, approximately 500 g within 15 cm of the soil surface is collected per soil sample and any plant debris is removed from the soil, after which it passed through a 2 mm sieve. A soil suspension is then prepared by adding 10 g of the sieved soil to 100 mL sterile distilled water and shaking at 150 rpm for 30 min. From this suspension, three serial 10-fold dilutions are prepared, of which 400 µL of each suspension is plated onto Petri plates containing modified FSM (Table 5). The inoculated plates are then incubated in the dark at 25 ◦ C and monitored for 3 weeks. Putative colonies of F. circinatum are transferred to medium for identification (described in Section 6.1 and Table 5). 5.5. Insect Samples Trapped insects are directly squashed onto F. circinatum selective medium (e.g., 50, 51) or subjected to sonication with subsequent plating onto one of the F. circinatum selective media [ 49 , 55 ]. F. circinatum isolates are identified based on micromorphological characteristics and DNA sequencing. Fourrier et al. [ 54 ] developed a method for the rapid detection of as few as 10 conidia of F. circinatum from a trapped beetle using a real-time PCR approach (described in Section 6.7). 6. F. circinatum Morphological Identification EPPO and IPPC have given general instructions for the identification of F. circinatum based on morphological features of mycelia [29,30]. 6.1. Culture Media for the Identification of F. circinatum In order to morphologically identify F. circinatum and to differentiate it from other species in the Fusarium fujikuroi species complex (FFSC) [ 63 , 64 ], isolates should be grown on several media (Table 5). These include Spezieller-Nährstoffarmer agar (SNA) [ 65 ] and Carnation Leaf Agar (CLA) [ 66 , 67 ]. For the examination of pigmentation and colony morphology, PDA is used, while complete medium and Carrot agar are typically used for sexual compatibility tests (Table 5) [31]. 6.2. Characters Associated with the Sexual Stage of F. circinatum All fungi in the FFSC, including F. circinatum, are heterothallic and require isolates of opposite mating type for completing the sexual stage [ 68 ]. All isolates of the fungus harbor either the MAT1-1 or MAT1-2 “idiomorphs” at the mating type locus; the mating type of an isolate can thus be diagnosed Forests 2019,10, 723 17 of 27 using PCR-based approaches [ 69 , 70 ]. A fertile cross between an isolate presumed to be F. circinatum with a standard tester strain for the species further provides strong evidence of conspecificity [ 31 ]. Because these tester strains are hermaphrodites, they may be used routinely as the female-fertile partner in laboratory crosses with field isolates that are commonly male-fertile [ 31 ]. Spores produced by the presumptive strain grown on Complete medium are typically used to fertilize a Carrot agar culture of the mating tester strain (Table 5) [31]. When cultivated on Carrot agar, perithecia produced by F. circinatum are ovoidal to obpyriform, non-papillate and slightly warted around the apex. They can be superficial or immersed, non-stromatic and have a dark purple color in water and 3% KOH, becoming red in 100% lactic acid. Neither ostiolar canals nor periphyses are formed. The cylindrical asci have an apex with a shallow, refractive ring. The ascospores are ellipsoidal to fusiform, smooth, hyaline and septate, with additional septa developing after discharge when they turn pale brown [ 63 , 71 ]. It should be noted, however, that the sexual stage of F. circinatum has never been observed under field conditions. 6.3. Characters Associated with the Asexual Stage of F. circinatum For identification purposes, Fusarium (F. circinatum and other Fusarium species) colonies are sub-cultured on SNA medium [ 29 , 65 ] that may be supplemented with two pieces of sterile paper [ 72 ]. This medium is used to produce phialides, microconidia and sterile hyphae (distinctly or not distinctly coiled), while CLA can be used to produce uniform macroconidia and the evaluation of sporodochial color [ 31 ]. These structures are produced in SNA after ca. 10 days, and on CLA after ca. 20 days, at 25 ◦C in the dark and are visible using bright-field microscopy at 400×magnification. In order to study colony morphology and pigmentation of the fungus, isolates should be grown on PDA and incubated at 22 ◦ C ± 6 ◦ C under near UV light or in daylight for ten days [ 30 ]. On PDA, F. circinatum grows quite rapidly, approx. 4.7 mm/day at 20 ◦ C [ 63 ] but ranging from 2.5 to 9.0 mm/day [ 73 , 74 ]. The mycelium produced has entire margins, and white cottony or whitish aerial mycelium with sometimes a salmon-colored tinge in the middle but often producing a pigment in the agar that could range from purple to dark violet or even yellow [13,30,31]. Asexual structures (i.e., macroand microconidia, Figure 2a–c,e and conidiogenous cells; polyphialides and monophialides, Figure 2a,b) are produced by F. circinatum both in culture and on plant tissues. Phialides (i.e., specialized conidiogenous cells that produce conidia in chain succession) of the aerial conidiophores are cylindrical and can be both monoand polyphialidic [ 75 , 76 ]. In order to study the type and shape of asexual structures, isolates must be grown on SNA for 10 days at 22 ◦ C ± 6 ◦ C under near UV light or in daylight. After that time, isolates are examined and compared to the F. circinatum descriptions of Nirenberg and O’Donnell [ 63 ], Britz et al. [ 71 ] and Leslie and Summerell [31]. On SNA, sclerotia are absent. Microconidia are aggregated in false heads (not in chains), with branched and erect conidiophores that can end in one or two phialides (Figure 2e). The microconidia in the aerial mycelium are usually obovoid, seldom oval and mostly non-septate or occasionally one-septate: (7.0 − )8.5 − 9.7 − 10.9( − 12.0) × (2.5 − )2.8 − 3.2 − 3.6( − 3.9) µ m [ 63 ]. Macroconidia are cylindrical, mostly three-septate, with slightly curved walls, an apical cell that narrows to an inwardly (i.e., toward the ventral side) curved tip, and a foot-shaped basal cell: (32.0 − )33.7 − 38.2—42.7( − 48.0) × (3.2 − )3.4 − 3.6—3.7( − 3.8) µ m [ 63 ]. Chlamydospores are absent [ 13 , 29 , 30 , 63 ], although many other Fusarium species have chlamydospores. However, some F. circinatum isolates produce swollen hyphae that may be confused superficially with chlamydospores or pseudochlamydospores [31]. On CLA, sporodochia with macroconidia are sparse and may be difficult to find. When found, they are usually on carnation leaf pieces and are pale orange in color. Macroconidia are slender, thin-walled, usually three-septate and typical of those produced by most species in the FFSC. Microconidia are abundant in the aerial mycelia, being obovoid, oval or allantoid in shape, non-septate and borne on monoand polyphialides which may proliferate extensively [31]. Forests 2019,10, 723 18 of 27 F. circinatum produces coiled sterile hyphae on both SNA and CLA during incubation in the dark [ 63 , 77 ], but these structures are more easily and reliably observed on SNA [ 13 ] (Figure 2d). The species’ epithet “circinatum” refers to these structures. The production of these distinctive flexuous/sinuous sterile hyphae used to distinguish F. circinatum from other species in the FFSC. However, a number of F. circinatum isolates from a wide geographical range (Europe, America, Africa, and Asia) and different mating types were recently found with sterile hyphae which were not distinctively coiled or absent, indicating that coiled hyphae are not a fully reliable attribute for the diagnostic of the species [ 72 , 74 ]. Thus, it is recommended that the morphological identification of F. circinatum is verified with molecular tools [30]. Forests 2019, 10, x FOR PEER REVIEW 19 of 28 °C ± 6 °C under near UV light or in daylight. After that time, isolates are examined and compared to the F. circinatum descriptions of Nirenberg and O’Donnell [63], Britz et al. [71] and Leslie and Summerell [31]. On SNA, sclerotia are absent. Microconidia are aggregated in false heads (not in chains), with branched and erect conidiophores that can end in one or two phialides (Figure 2e). The microconidia in the aerial mycelium are usually obovoid, seldom oval and mostly non-septate or occasionally oneseptate: (7.0−)8.5 − 9.7 − 10.9(−12.0) × (2.5−)2.8 − 3.2 − 3.6(−3.9) μm [63]. Macroconidia are cylindrical, mostly three-septate, with slightly curved walls, an apical cell that narrows to an inwardly (i.e., toward the ventral side) curved tip, and a foot-shaped basal cell: (32.0−)33.7 − 38.2—42.7(−48.0) × (3.2−)3.4−3.6—3.7(−3.8) μm [63]. Chlamydospores are absent [13,29,30,63], although many other Fusarium species have chlamydospores. However, some F. circinatum isolates produce swollen hyphae that may be confused superficially with chlamydospores or pseudochlamydospores [31]. On CLA, sporodochia with macroconidia are sparse and may be difficult to find. When found, they are usually on carnation leaf pieces and are pale orange in color. Macroconidia are slender, thinwalled, usually three-septate and typical of those produced by most species in the FFSC. Microconidia are abundant in the aerial mycelia, being obovoid, oval or allantoid in shape, nonseptate and borne on monoand polyphialides which may proliferate extensively [31]. F. circinatum produces coiled sterile hyphae on both SNA and CLA during incubation in the dark [63,77], but these structures are more easily and reliably observed on SNA [13] (Figure 2d). The species’ epithet “circinatum” refers to these structures. The production of these distinctive flexuous/sinuous sterile hyphae used to distinguish F. circinatum from other species in the FFSC. However, a number of F. circinatum isolates from a wide geographical range (Europe, America, Africa, and Asia) and different mating types were recently found with sterile hyphae which were not distinctively coiled or absent, indicating that coiled hyphae are not a fully reliable attribute for the diagnostic of the species [72,74]. Thus, it is recommended that the morphological identification of F. circinatum is verified with molecular tools [30]. Figure 2. Morphological characters of F. circinatum (A) monophialides on Spezieller-Nährstoffarmer Agar (SNA) (B) polyphialides on SNA (C) microand macroconidium on Carnation Leaf Agar (CLA) (microconidia are also visible in a, b and e) (D) Fusarium circinatum coiled sterile hyphae on SNA (E) Fusarium circinatum microconidia growing in false heads on SNA. Spore sizes are given in the text. 6.4. Maintenance and Conservation of F. circinatum Isolates As in the case of most filamentous fungi, F. circinatum can be maintained on artificial media as a short-term preservation method, but losses in virulence, pathogenicity and sporulation may occur D E Figure 2. Morphological characters of F. circinatum ( A ) monophialides on Spezieller-Nährstoffarmer Agar (SNA) ( B ) polyphialides on SNA ( C ) microand macroconidium on Carnation Leaf Agar (CLA) (microconidia are also visible in a, b and e) ( D )Fusarium circinatum coiled sterile hyphae on SNA ( E ) Fusarium circinatum microconidia growing in false heads on SNA. Spore sizes are given in the text. 6.4. Maintenance and Conservation of F. circinatum Isolates As in the case of most filamentous fungi, F. circinatum can be maintained on artificial media as a short-term preservation method, but losses in virulence, pathogenicity and sporulation may occur with repetitive subculturing (e.g., [ 78 , 79 ]). For long-term preservation of fungal cultures, immersion of the mycelium or spores of the fungus in sterile distilled water is one of the simplest methods [ 80 ]. However, since the stability of fungal cells was not ensured by this simple procedure [ 81 ], other methods have been suggested. For instance, the maintenance of cultures under a layer of mineral oil has been used for many years as a method to reduce growth and extend the time interval between transfers to fresh media [ 82 ]. This technique could be a good option for fungi that do not tolerate freeze drying, or where cryogenic storage is not possible [78]. There are other methods which are more appropriate and with higher success rates. For example, Windels et al. [ 83 ] succeeded in preserving different Fusarium spp. on soil for 5 years. The authors suggested that the storage temperature of 4.5 ◦ C rather than room temperature explained the higher viability of the isolates after the preservation period. One of the inconveniences of storage in soil is that Fusarium cultures colonize the substrate, and there is consequently a chance of cultural variation [ 84 ]. For this reason, using silica gel rather than soil is preferred, since cultures do not colonize this alternative substrate [ 83 ]. Furthermore, it has been reported that not all Fusarium spp. remain viable in soil [ 66 ]. Although the silica gel technique is not as effective as freeze-drying or liquid-nitrogen storage (see the last paragraph of this section), it is considered a useful alternative for laboratories with limited Forests 2019,10, 723 19 of 27 resources or those requiring a simple technique [ 82 ]. Cereal grains are recognized as another suitable substrate for the preservation of fungal cultures. However, as is the case with soil, they do not prevent fungal metabolism and growth, and thus, risks of physiological and genetic change exist [83]. Although a variety of methods can be used to store Fusarium spp. and other fungal cultures, cryopreservation in liquid nitrogen and lyophilization are the methods recommended and used in most recognized laboratories, such as the American Type Culture Collection [ 81 ]. The colder the storage temperature and the higher the temperature stability, the greater the likelihood for long-term viability [ 78 , 85 ]. To increase the viability of the cultures after preservation by lyophilization, isolates should be grown on CLA in Petri dishes for 7–10 days. Several colonized carnation leaf pieces are then transferred to sterile vials, and 0.5 mL of sterile skim milk can be added to each vial as an additional cryoprotective substance before lyophilization [ 66 ]. The recommended storage temperature for lyophilized cultures is 5 ◦ C or lower, but some fungus cultures are stored at temperatures as low as − 52 ◦ C [ 66 ]. A simpler and less expensive alternative to conventional freeze-drying methods, but one that is similar in efficacy, particularly with Fusarium spp., is the modified filter paper method described by Fong et al. [ 86 ]. This methodology was found to be very effective (100% of isolates were viable after four years) for preservation of F. oxysporum cultures at 19 ◦ C. F. circinatum can also be preserved using cellulose paper (personal communication by J. Diez). 6.5. Molecular Methods for Pathogen Detection The symptoms caused by F. circinatum, particularly in seedlings, stems and shoots may be similar to those caused by several other pathogenic fungi, such as Sphaeropsis sapinea (Fr.) Dyko & B. Sutton, Gremmeniella abietina (Lagerb.) M. Morelet, Pachyramichloridium pini (de Hoog & Rahman) C. Nakash., Videira & Crous, Crumenulopsis sororia (P. Karst.) J. W. Groves, Cenangium ferruginosum Fr. and Caliciopsis pinea Peck. In addition, needle symptoms may resemble those caused by species of Dothistroma,Cyclaneusma,Lecanosticta, Lophodermium and Lophodermella (although the defoliation caused by these species is not as severe as in the case of F. circinatum that causes dieback of whole branches and shoots). Botrytis spp. also cause similar needle blight in pine seedlings. It is consequently important to confirm the agent causing symptoms resembling those of F. circinatum by laboratory analysis. The Pine pitch canker field guide of the EU COST Action FP1406 PINESTRENGTH describes the above-mentioned pathogens causing symptoms similar to F. circinatum in more detail (http://www.pinestrength.eu/2018/04/12/disseminationpitch-canker-field-guide-wg-1-pamphlet/). When strains suspected to be F. circinatum are obtained after isolation from plant tissue, their identity can be determined by species-specific PCR [ 43 , 72 , 87 ] or by sequence and phylogenetic analysis of several markers, such as the Translation Elongation Factor 1 alpha (Tef1) gene [ 88 ]. As an alternative to isolation in pure culture, F. circinatum can be detected directly in planta by conventional PCR and real-time or quantitative PCR (qPCR) using SYBR Green or hydrolysis probes (see Sections 6.6 and 6.7). Similar techniques have been also described to detect trapped airborne propagules of F. circinatum [ 43 , 44 ]. A recent collaborative study joined 23 partners to assess the transferability and performance of nine different protocols (conventional PCR and real-time PCR) using a wide panel of F. circinatum and other Fusarium spp. DNA [89]. 6.6. Diagnosis Using Conventional PCR The first species-specific PCR test for the detection of F. circinatum was developed by Schweigkofler et al. [ 43 ]. The PCR primers target specific regions located in the ribosomal RNA (rRNA) Intergenic Spacer (IGS). The test was initially designed to be used in a real-time PCR protocol using SYBRGreen as a DNA staining dye, but could alternatively be used in conventional PCR. Although the test proved to be specific at the time of the study, the authors recommended sequencing the PCR amplicon to check for cross reactions with DNA of as yet unknown but closely related cryptic species. Annex 4 of the EPPO diagnostic protocol PM7/91 [ 29 ] for F. circinatum proposed a modified version of the Schweigkofler et al. test in which the final MgCl 2 concentration of the PCR reaction is Forests 2019,10, 723 20 of 27 decreased to 2 mM, instead of the 5 mM used in the original article, and for which the test is run in conventional PCR. Despite a lower final MgCl 2 concentration increasing the specificity of the reaction, the modified protocol proposed in PM7/91 also recommended that any positive result should be confirmed by amplicon sequencing and comparison to reference sequences by BLAST analysis on GenBank. PM7/91 recommends this modified protocol for the direct detection of F. circinatum in plant tissue, including seeds. Another conventional PCR assay was developed by Ramsfield et al. [ 87 ]. This test works in a multiplex fashion, and two loci of unknown function are targeted to be co-amplified if F. circinatum DNA is present. This test may be used to detect F. circinatum in plant, soil or potting mix. Since the test requires the simultaneous amplification of two unrelated but specific regions of the F. circinatum genome, it has been suggested that it brings additional reliability. The conventional PCR tests described above are easy to set up and need less expensive equipment than qPCR methods, but require an additional electrophoresis step, and thus, more time to obtain a result [89]. 6.7. Diagnosis Using qPCR Several protocols targeting F. circinatum have been developed in the past ten years which take advantage of real-time PCR technologies and reduce turnaround time for analysis. Whether using a double-stranded DNA staining dye such as SYBR Green or a specific hydrolysis probe (also called “double-dye”, “TaqMan ® ”, or “dual-labelled”), these technologies bring an additional level of specificity due to specific binding of the probe or melting curve analysis of the SYBR Green stained DNA of the PCR product. Dreaden et al. [ 90 ] and Fourie et al. [ 44 ] proposed a real-time PCR protocol targeting specific regions of the IGS of the rDNA. The test of Fourie et al. [ 44 ] was particularly optimized to detect F. circinatum conidia in traps set up in nurseries and to measure airborne inoculum pressure. These protocols work in real-time but require an additional melting curve analysis of the PCR products at the end of the run. The melting temperature (Tm) of the amplicons (i.e., the so-called denaturation peaks) is measured and compared to that of the positive control. The Tm is a function of the size and the sequence composition of the amplicon; therefore, by comparing the Tm of the positive control to those of the unknown DNA samples, it is possible to confirm a positive result. SYBR Green real-time PCR requires real-time PCR equipment, but it involves less costly reagents than hydrolysis probe technology. Nevertheless, interpretation of the data is not always straightforward, and the Tm of the denaturation peaks is sometimes variable. An additional level of specificity was achieved by Ioos et al. [ 47 ] using a probe that was initially designed in the IGS region to detect minute amounts of F. circinatum DNA in pine seeds, after a biological enrichment step. This test was later adapted to detect F. circinatum from potential insect vectors [ 54 ]. Lamarche et al. [ 91 ] proposed an alternative assay also targeting the IGS region, which was validated with seeds, woody tissue and insects. Another locus in the F. circinatum genome was targeted by Luchi et al. [ 92 ], who used the Tef1 gene to develop a duplex real-time PCR test for the simultaneous detection of the pine pitch canker pathogen and Caliciopsis pinea in pine woody tissues. This test may be useful since both pathogens share the same ecological niche on Monterey pine causing similar bleeding canker symptoms, especially at the early stage of colonization. 6.8. Specificity of DNA-Based Tests Given the importance of F. circinatum, a quarantine fungus for several countries, diagnostic tests utilized must provide reliable results, with a particular emphasis on specificity. F. circinatum belongs to the American clade of the FFSC [ 64 , 76 ], which accommodates many geneticallyand morphologically-related species. New species in this clade are continuously being described, such as the new pine pathogenic species F. marasasianum Herron, Marinc. & M. J. Wingf., F. parvisorum Herron, Marinc. & M. J. Wingf., and F. sororula Herron, Marinc. & M. J. Wingf. [ 93 ]. It is therefore of great importance that the specificity of each test published is continuously re-assessed in light of Forests 2019,10, 723 21 of 27 the current genetic diversity of the FFSC. It is also recommended that several tools targeting specific, but different parts of the F. circinatum genome are used in a complementary way in order to confirm the diagnosis, and/or that the specific amplicons are sequenced to verify the result. In addition to existing tests targeting known taxonomic markers, several other F. circinatum-specific regions have been unraveled by in silico analysis, and these putative genes should be used for the development of new detection tools, either by PCR, real-time PCR or LAMP analysis [ 94 ]. Inclusivity (i.e., ability to target all F. circinatum strains) and specificity (i.e., ability not to cross-react with non-target species) of the currently available molecular detection tools targeting F. circinatum have been recently assessed and compared [ 89 ]. Overall, the study demonstrated that current diagnostic protocols for the detection of F. circinatum is not easily transferable, and that end-users should perform validation tests, especially under modified conditions, such as different reagents and/or equipment, prior to use. 7. Global Situation Due to early detection, constant surveillance and control measures, F. circinatum outbreaks are considered officially eradicated in France and Italy (https://gd.eppo.int/taxon/GIBBCI/distribution). The outbreaks in France occurred on P. menziesii and Pinus spp. nurseries and gardens [ 10 , 95 – 97 ], and in Italy in urban parks on Aleppo pine (P. halepensis Mill.) and Italian stone pine (P. pinea L.) [ 9 ]. F. circinatum is widely established in northern Spain (Galicia, Cantabria, Navarra and Basque Country), mainly affecting Monterey pine plantations, but it is also present in maritime pine stands (Drenkhan et al., unpublished). In Portugal, F. circinatum was exclusively reported from nurseries for years, but was also recently detected in mature trees from a Monterey pine plantation. However, all trees were destroyed and the surrounding area intensively surveyed, and the pathogen has not been detected since (H. Bragança, personal communication). From an epidemiological point of view, it is highly problematic that F. circinatum can persist as a latent endophyte in several plant species, including conifers such as Picea and Larix that are not regulated in the EU legislation [19]. The introduction of F. circinatum into new environments has in some countries led to more severe epidemics. For example in South Africa, F. circinatum was detected in 1990 from a single nursery in the Mpumalanga province [ 5 ]. Since then, it has been detected in various forestry nurseries across South Africa, causing seedling disease as well as field establishment problems [ 98 – 100 ]. Fifteen years later, in 2005, F. circinatum was reported on established plantation trees for the first time [ 101 ]. Today, it is a problem in the coastal and mountain regions of the Western and Eastern Cape, as well as in the KwaZulu-Natal midlands, causing disease on Monterey pine and Gregg’s pine (P. greggii Engelm. Ex Parl.) [ 102 , 103 ]. More recently, however, pitch canker was also detected in the Limpopo province on mature P. patula [ 104 ]. This report is of significance to South Africa, since Mexican weeping pine (P. patula Schiede ex Schltdl. & Cham.) is the most widely planted species in the country. If one considers the origin and movement of F. circinatum by studying the genetic makeup of populations, it is clear that populations appear to be interconnected, but also diverse and different. Overall, the results suggest that multiple introductions and subsequent movement (either between plantations or from planting material) are responsible for the presence of pitch canker in South Africa. 8. Conclusions F. circinatum is listed among the species recommended for regulation as quarantine pests in Europe, and the EFSA considers the probability of new introductions into the EU very likely. Each country has adapted its survey program according to the presence or absence (and proximity) of the pathogen, tree species distribution and environmental conditions. This results in large differences in the number of surveys and samplings conducted at different sites hosting susceptible species. Laboratory methods used for pathogen detection are also diverse but mostly based on EPPO recommendations. The global spread of F. circinatum in the relatively recent past suggests that the pathogen will continue to be encountered in new environments in the future. The ease with which F. circinatum has moved globally also suggests that new genotypes of the pathogen will be introduced to new Forests 2019,10, 723 22 of 27 areas, including those where the pathogen already occurs. In some areas, such as those where plantation forestry based on non-native species is practiced, this will result in lost productivity. Clearly, continuous surveillance of reproductive material (seed and seedlings), nurseries, plantations and forests, prompt control measures, and realistic contingency plans (PLURIFOR, 2019; https: //plurifor.efi.int/es/chancro-resinoso-del-pino/) are of the utmost importance in Europe and elsewhere to limit disease spread. It is important to recognize that new disease outbreaks in countries outside Europe are also relevant to European countries. In this regard, the “bridgehead effect”, where new introductions of a tree pathogen become increasingly likely as new environments are invaded, must be considered [105]. Author Contributions: All authors contributed to original draft preparation, review and editing of the article. Funding: This article is also based upon work carried out during COST Action FP1406 PINESTRENGTH (Pine pitch canker-strategies for management of Gibberella circinata in greenhouses and forests), supported by COST (European Cooperation in Science and Technology). This study was supported by project AGL2015-69370-R “Nuevas tecnolog í as de secuenciaci ó n para el estudio de los micovirus en Fusarium circinatum” (MINECO/FEDER, UE). This work is a contribution of URGENTpine (PTDC/AGR-FOR/2768/2014) funded by Fundaç ã o para a Ci ê ncia e a Tecnologia, I.P., through national funds, and the co-funding by the FEDER (POCI-01-0145-FEDER-016785), within the PT2020 Partnership Agreement and Compete 2020. Thanks are due for the financial support to CESAM (UID/AMB/50017/2019), to FCT/MEC through national funds, and the co-funding by the FEDER, within the PT2020 Partnership Agreement and Compete 2020. FCT also supported J.M.-G. (SFRH/BPD/122928/2016). The Forestry Commission UK provided financial support for M.M. and K.T. Acknowledgments: Tiziana Baschieri (Servizio Fitosanitario Regione Emilia Romagna), who is the national coordinator for surveillance of Fusarium circinatum in Italy, is warmly acknowledged for providing summary data for the Italian territory. Dina Ribeiro from the Portuguese Forest Authority is thanked for providing data from Portugal. Odile Colnard from the French Ministry of Agriculture, is thanked for providing data for France. Kristof Capieau from the Swedish Board of Agriculture is thanked for providing data for Sweden. Conflicts of Interest: The authors declare no conflict of interest. References 1. Alonso, R.; Bettucci, L. 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