EPPO Global Database

Fusarium circinatum(GIBBCI)

EPPO Datasheet: Fusarium circinatum

Last updated: 2021-01-28


Preferred name: Fusarium circinatum
Authority: Nirenberg & O'Donnell
Taxonomic position: Fungi: Ascomycota: Pezizomycotina: Sordariomycetes: Hypocreomycetidae: Hypocreales: Nectriaceae
Other scientific names: Fusarium lateritium f. sp. pini Hepting, Fusarium subglutinans f. sp. pini Hepting, Gibberella circinata Nirenberg & O'Donnell
Common names in English: pitch canker of pine
view more common names online...
EPPO Categorization: A2 list
EU Categorization: Emergency measures, A2 Quarantine pest (Annex II B)
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HOSTS 2021-01-15

Fusarium circinatum infects mainly Pinus spp. It has been reported to infect 106 different host species, including 67 Pinus species, 18 Pinus hybrids, 6 non-pine tree species, and 15 grass and herb species which are hosts under natural conditions or show symptoms after artificial inoculation (Drenkhan et al., 2020). In North America, its main native hosts are Pinus elliottii, P. palustris, P. patula, P. radiata, P. taeda, P. virginiana and P. muricata. Host species are available throughout the European territory, including the European and Mediterranean species Pinus halepensis, Pinus pinaster, Pinus sylvestris, and various North American species planted in Europe such as Pinus contorta and Pinus strobus, and certain Asian species (e.g. Pinus densiflora, Pinus thunbergii). There is an isolated record on Pseudotsuga menziesii, not apparently associated with any damage, while infection on Larix spp. is based on greenhouse data.

Host list: Agrostis capillaris, Arrhenatherum longifolium, Briza maxima, Bromus carinatus, Centaurea decipiens, Cymbidium sp., Ehrharta erecta, Holcus lanatus, Hypochaeris radicata, Lolium arundinaceum, Musa acuminata, Pentameris pallida, Pinus arizonica, Pinus armandii, Pinus attenuata, Pinus ayacahuite, Pinus canariensis, Pinus cembroides, Pinus contorta, Pinus coulteri, Pinus densiflora, Pinus discolor, Pinus douglasiana, Pinus durangensis, Pinus echinata, Pinus elliottii var. densa, Pinus elliottii var. elliottii, Pinus elliottii, Pinus glabra, Pinus greggii, Pinus halepensis, Pinus hartwegii, Pinus kesiya, Pinus leiophylla, Pinus luchuensis, Pinus maximinoi, Pinus montezumae, Pinus muricata, Pinus nigra, Pinus occidentalis, Pinus palustris, Pinus patula, Pinus pinaster, Pinus pinea, Pinus ponderosa, Pinus pringlei, Pinus pseudostrobus, Pinus radiata, Pinus rigida, Pinus sabiniana, Pinus strobus, Pinus sylvestris, Pinus taeda, Pinus tecunumanii, Pinus teocote, Pinus thunbergii, Pinus torreyana, Pinus virginiana, Pseudotsuga menziesii, Rubus ulmifolius, Sonchus oleraceus, Teucrium scorodonia, Zea mays


The origin and spread of F. circinatum are obscure. Older records from various parts of the world may be based on inadequate identification. Outside America, records in Japan, South Africa and Spain are considered to result from introductions. Based on genetic diversity indices, the fungus is probably native in North America, most likely Mexico (Wikler & Gordon, 2000), with further range expansion first in Eastern North America (Hepting and Roth, 1946) and then in the Western USA, specifically California (McCain et al., 1987). The fungus has probably been moved around the world with pine planting stock, seedlings and especially infected seed. Until 2005, there have been no reliable records in the EPPO region. In Spain and Portugal, outbreaks were first detected in nurseries, and in France it has been found in conifer seeds imported from the USA. In Northern Spain and some areas of Portugal, where the pest is now established, it has been found both in nurseries and in forest stands of Pinus radiata, P. pinaster, P. nigra, P. pinea and P. sylvestris (Landeras et al., 2005, Pérez-Sierra et al., 2007; Bragança et al., 2009; EPPO, 2019a). The outbreaks in Italy (Carlucci et al., 2007) and France (EPPO, 2006) have now been officially eradicated.   Spanish populations are significantly differentiated and structured into two distinct groups suggesting two independent introductions (Berbegal et al., 2013). 

The world distribution of pitch canker is largely confined to Mediterranean and sub-tropical climates, with some extension into temperate climates, suitability tends to decrease from the coastal areas to the centre of Europe, being most suitable or optimal in parts of Northern and Eastern Spain, Central and Northern Portugal and the coastal areas of France, Italy and Greece (Ganley et al., 2009; EFSA, 2010; Möykkynen et al., 2015). In the EPPO region, host availability is not a limiting factor for the spread of F. circinatum, however the pathogen is reported to stop its growth and sporulation as temperatures approach zero Celsius. For this reason, it is presumed that areas with Mediterranean and warm Oceanic climates may be more favourable to the pathogen than continental climates.

EPPO Region: Portugal (mainland), Spain (mainland)
Africa: South Africa
Asia: Japan (Kyushu, Ryukyu Archipelago), Korea, Republic
North America: Mexico, United States of America (Alabama, Arkansas, California, Florida, Georgia, Louisiana, Mississippi, North Carolina, South Carolina, Tennessee, Texas, Virginia)
Central America and Caribbean: Guatemala, Haiti
South America: Brazil (Santa Catarina), Chile, Colombia

BIOLOGY 2021-01-15

F. circinatum is a pathogen which is seed-borne, airborne and also found on insects. It can infect vegetative and reproductive parts at all ages of the host. In Pinus halepensis in California, the pathogen was found causing significant resin soaked cankers on the primary roots and root collars of planted adult trees (Garbelotto & Schweigkofler, 2007). It can also infect pine seeds internally or be present as a superficial contaminant (Barrows-Broaddus & Dwinell, 1985; Storer et al., 1998, Elvira-Recuenco et al., 2015), but it is not known how this infestation occurs. Seed-borne inoculum can infect and kill pine seedlings. Since perithecia have not been observed in nature, it is presumed that ascospores are not of great importance for infection of the host, however sexual reproduction may imply genetic recombination, which can lead to the emergence of strains with enhanced virulence. Most infection is by macroconidia and/or microconidia, carried by splashed rain, wind or insects. Bark-feeding insects (e.g. Pityophthorus sp., Ips sp., Conophthorus sp.) commonly breed in affected branches and emerging adults commonly carry the pathogen although their vectoring potential is still undemonstrated, given that most papers prove phoresy and not vectoring (Brockerhoff et al., 2016). Nonetheless it has been suggested that these insects may increase infection by wounding their hosts (Sakamoto & Gordon, 2005). Wound-associated infection is reported to be important, however a recent study demonstrated that F. circinatum is also able to colonize seedlings stem and tree branches that were artificially inoculated without wounds (Swett et al., 2018). F. circinatum is mainly characterized by necrotrophic behaviour but also displays hemibiotrophic behaviour, being capable of living inside the host remaining symptomless in seedlings for more than a year and in the roots of mature trees (Elvira-Recuenco et al. 2015; Swett et al., 2016; Hernandez-Escribano et al., 2018a).

Moisture is required for an infection to occur, and infections appear to be associated with locations or seasons where atmospheric moisture is readily available and temperatures are relatively warm, such as in the South-Eastern USA during summer thunderstorms (Dwinell et al., 1985). In California, the disease is most severe in close proximity to the coast. The distribution of the disease also suggests that cooler temperatures are restrictive (Gordon et al., 2001). At moderate temperatures, the pathogen can survive for 1 year or more in infected wood, although new sporulation is greatly decreased or non-existent when trees are dead (Garbelotto et al., 2008) The highest density of the aerial inoculum in Northern California was found during the warm (15-20 °C), rainy months of the year (Garbelotto et al. 2008), but sporulation stops as minimum temperatures approach freezing.  It seems that the positive effect of temperature on spore germination is opposite to the effect on spore production in Galicia, Northern Spain (Dvorák et al., 2017). In established infestations most new infections occur via microconidia (Schweigkofler et al. 2004).



In seedlings, the pathogen typically rots the hypocotyl at or near the soil-line, so that the seedling collapses. Seedlings may also show necrosis, chlorosis, wilting and dieback. Seedlings may also be infected by soil-borne inoculum. In either case, the symptoms are not particularly distinctive, differing little from those caused by other damping-off pathogens. Root infections are most often observed on seedlings in nurseries or Christmas tree farms, but can also occur on exposed roots of larger trees in landscape plantings. In Christmas tree farms, the pathogen may extensively colonize the root system, causing a brown discoloration and disintegration of the cortex. Above-ground symptoms are generally not apparent until the pathogen has reached the root crown and girdled the stem (Garbelotto & Schweigkofler, 2007). This disease stage results in a uniform loss of colour in the foliage, which fades first to a dull green, then yellow and finally brown. Removal of the bark on the main stem near the soil-line may reveal resin-soaked tissue with a honey-brown to dark-brown discoloration (pitching).

Branches and stems of pine trees of any age may also be infected. Infection usually begins as a canker and dieback of small branches in the top or middle part of the tree. Needles wilt above the infection site becoming chlorotic, then turn red and brown and resin accumulates on the branch surface. Repetition of these symptoms throughout the canopy may lead to extensive dieback. Branch infection always precedes trunk infection, however, the trunk and larger branches may in due course be infected, producing copious amounts of resin and accelerating the decline of the tree. Girdling of the main stem may lead to death of the tree. Death of infected trees can be hastened by bark beetle attacks. In California, a significant percentage of P. radiata trees can recover, hence, the presence of canopies in clear remission among dead and dying canopies can also be taken as a stand-level trait associated with established outbreaks of itch Canker (Bonello et al., 2001).


In culture, F. circinatum produces macro- and microconidia (Nirenberg & O’Donnell, 1998). Macroconidia are typically 3-septate, with slightly curved walls, 32–48 × 3.3–3.8 µm, resembling those of numerous other anamorphs in the form-genus Fusarium. Microconidia, typically single-celled, ovoid (or nearly oval or allantoid), are borne in false heads on aerial polyphialides. The proliferation of microconidiophores, coupled with a slight twisting of the aerial mycelium on which they are borne, gives a distinctive colony morphology. Aerial mycelium is white or slightly violet. Colonies are frequently sectored. These characters do not clearly separate F. circinatum from other fungi with anamorphs of the Fusarium subglutinans groupThe sterile hyphae (coiled or not distinctively coiled) are characteristic of F. circinatum and are observed clearly on Spezieller-Nährstoffarmer Agar (SNA) medium. The epithet ‘circinatum’ refers to these typical coiled hyphae, also called ‘circinate’ hyphae (EFSA, 2010; EPPO 2019b). However recent studies show that coiled hyphae are not a fully reliable attribute for the diagnostic of the species (Vainio et al., 2019). Perithecia are also readily produced in culture: dark purple to black, ovoid to obpyriform, 332–396–453 µm high and 288–337–358 µm wide (Britz et al., 2002), asci are cylindrical, 88–100 × 7.5–8.5 µm, released by oozing; ascospores, 1-septate, are 8 per ascus and ellipsoidal to fusiform shaped. This description is close to that of many related species. 

Detection and inspection methods

Since some pathogens cause symptoms very similar to F. circinatum, laboratory analysis should always be carried out to identify and confirm its presence. Correll et al. (1991) describe a suitable selective medium. The COST Action Field Guide of Pine Pitch Canker (2017) provides an overview of damage that is similar to the symptoms caused by F. circinatum. Sampling protocols for seeds, seedlings, twigs, branches, shoots, soil samples, spore traps and insects from different studies are collated and compiled by Vainio et al., 2019 as well as morphological and molecular identification methods. Identification of F. circinatum from samples of Pinus spp. or Pseudotsuga menziesii (plant tissue or seeds), morphological and molecular methods are available also and described in detail in the IPPC Diagnostic Protocol (Annex 22) of ISPM 27 (FAO, 2017) and EPPO Diagnostic Protocol PM 7/91 (EPPO, 2019b). Molecular methods are the preferred methods for the identification of F. circinatum because of their sensitivity and accuracy. However, Ioos et al. (2019) highlighted that the use of protocols using conventional or real-time PCR outside their initial development and validation conditions should require careful characterization of the performance data prior to use under modified conditions.  

A standard way of determining presence of the pathogen in an infested stand is that of performing tree bark spore washes followed by culturing on selective media: at that point identification can be done either by morphology or using molecular assays. Early detection based on symptoms is almost impossible in a forest stand, given the rarity of symptoms. Methods based on the trapping of spores on filter paper, followed by PCR-based detection performed directly on washes of the filter have proven to be among the most effective methods for early detection of the pathogen (Schweigkofler et al. 2004). This method has been employed with success by many national phytosanitary agencies around the world.


F. circinatum is spread locally by splashing water, wind and insects, but its rate of spread in newly infested areas does not appear to be very high.  Garbelotto et al. (2008) report a distance of 2 km/year as the potential of spread in California, based on spore detection. In general, the natural spread of the pathogen may be limited due to the short dispersal distances of the spores and possibly by the fairly short flight distances of disseminating insects (Zamora-Ballesteros et al., 2019). 

Over long distances, F. circinatum can be carried by consignments of pine seeds or pine cones, or by plants for planting. In California, the pathogen was established in San Diego County tens of kms away from any known natural infestations due to the planting of young Aleppo Trees in a parking lot (Garbelotto et al., 2007). These trees were about 10 years old when planted, and, at the time of planting, showed no obvious symptoms. The movement of infected Christmas trees has also been identified as significant pathway for the spread of the pathogen in California (Gordon et al., 2001). The long distance (California to New Zealand) movement of the pathogen was detected and eradicated in a lot of Douglas-fir seedlings, indicating that movement of non-pine live hosts could effectively move the pathogen long distances. Interestingly, the nursery of origin was, at the time of discovery, outside the official zone of infestation by the pathogen (Vogler et al., 2004). 

One significant pathway for the medium and medium-to-long range dispersal of the pathogen has been identified in the use of contaminated tools and equipment, in the movement of infected green waste and possibly in the use of contaminated pots and potting racks. Soil has also been shown to be infectious at least for short periods of time (Swett and Gordon, 2013; Camilli et al., 2013).

In principle, the pathogen could remain viable and be carried by infected wood, but this is most likely for particle wood made from small branches and their bark, in which spores of the fungus can survive. Round wood and sawn wood, especially if debarked, are less likely to carry the fungus. Additionally, in view of the substantial trade in pine wood, and the limited distribution of the fungus, the likelihood of a timber pathway of movement is low but not nil (EFSA, 2010; Kopinga et al., 2010). Wood packaging material made of coniferous wood also presents a risk because the wood used for packaging is usually of lower quality in terms of physical imperfections and presence of bark (Vainio et al., 2019). Long-range dispersal through the movement of soil is unlikely as the fungus cannot survive for long periods in the soil (Nirenberg and O’Donnell, 1998; Serrano et al., 2017). Numerous insect species that commonly occur in pine nurseries and forests throughout Europe and elsewhere have the potential to spread the fungus as either vectors, carriers or wounding agents. Most of the evidence is, however, circumstantial and ambiguous (Fernandez-Fernandez et al., 2019)


Economic impact

F. circinatum is a chronic problem in the South-Eastern USA, where it affects pine production in plantations, nurseries (Barnard & Blakeslee, 1980) and seed orchards (Dwinell et al., 1981; Dwinell et al., 1985), but does not have significant impacts on native forests. It regularly adds to the cost of production but does not result in large financial losses in most years. Most southern pines are affected to some extent, including P. taeda, which typically sustains only minor damage and P. elliottii, which can be more severely affected. Major epidemics were reported for this species in Florida in the 1970s, with an estimated loss of between 0,4 and 0,9 million cubic meters annually in the period from 1974 through 1979 (Dwinell et al., 1985). However, in recent times, the use of less susceptible genotypes and changes in silvicultural techniques have greatly reduced the impact of the disease in the South eastern USA. 

F. circinatum also occurs throughout the coastal regions of California, from San Diego in the south, to Mendocino County north of San Francisco (Gordon et al., 2001) Since F. circinatum was introduced into California in 1986, it has caused damage and mortality of P. radiata in urban areas and in native forests. Costs of tree removal and replacement may eventually amount to several million USD in severely affected areas (Templeton et al., 1997). Other Pinus spp. are also affected. In California, the disease has had a mild impact on all three native mainland stands of P. radiata. These represent the majority of the 5 native stands of this globally important pine species, hence this impact, even if limited, is of major concern. Pitch Canker has however had significant negative impacts on planted Monterey pines in urban settings, along roads, in golf courses and even in National Parks. It has also severely affected entire stands of P. muricata naturally regenerated after wildfires in Marin County (Swett and Gordon, 2013). Genetic diversity has been identified as an important aspect limiting damage by this pathogen (Aegerter et al. 2006), together with climatic (Garbelotto et al., 2008) and ecological factors. The impact has also been significant in plant nurseries and Christmas tree farms in California (Gordon et al. 2001).

The disease is considered as one of the most important diseases of conifers globally (Wingfield et al., 2008), Since its introduction into South Africa, F. circinatum has caused serious problems in seedling nurseries (Viljoen et al., 1994, 1995). The appearance of F. circinatum in plantations in Spain, South Africa, along with its presence in nurseries in Chile, substantially enhances this threat since these countries have large areas of P. radiata, and/or P. patula, both known to be very susceptible to the pathogen. In Europe, Spain has the largest area planted with this species (ca. 287 000 ha) which provides 25% of Spanish conifer timber. In Spain the disease is causing damage in forests and nurseries in five regions: Galicia, Asturias, Cantabria, País Vasco and Castilla y León. When dealing with native European species, Scots pine (P. sylvestris), P pinaster and Aleppo pine (P. halepensis) have been reported to be more susceptible than Austrian pine (P. nigra) and Italian stone pine (P. pinea) based on lab tests (Eneback & Stanosz 2003, Itturixta et al., 2012, 2013), however in the Iberian peninsula where both the exotic P. radiata and the native P. pinaster have been exposed to the pathogen, damage is significant only on the exotic, while it is minor on the native one. In Japan, Pitch Canker has been reported from Pinus luchuensis (Muramoto and Dwinell 1990), while P. densiflora appears to be less susceptible based on lab tests (Kim et al. 2008)


In the South-eastern USA, the F. circinatum problem is addressed by controlling the disease as far as possible in well managed seed nurseries, using less susceptible planting material, and preventing the spread of inoculum from infested areas by sanitary precautions (Dwinell et al., 1985). Chemical and biological control methods are ineffective or uneconomic, and have at present no particular role to play (except possibly seed treatment with fungicides). Nurseries and Christmas tree farms should be carefully sited. Clean, preferably local, seeds should be used. Wounding and over-fertilization should be avoided. In general, good hygiene should be maintained, and precautions taken for movement of equipment and soil. In plantations, infected material (logs, firewood) should not be moved: chipping or debarking may be used to reduce the risk that the pathogen may bespread by insects. Insecticide use to limit spread by insects is not environmentally appropriate nor was it effective when tried (Swett & Gordon, 2013).

Disease resistance and tolerance are key elements for the control of the disease, and resistant clones of P. radiata are available for replanting in areas of California affected by the disease (Aegerter 2003).  Likewise, very susceptible species should not be planted where risk of infection is high. -Large scale studies of American Pinus spp. (Hodge & Dvorak, 2000) have shown considerable differences among species in susceptibility. P. radiata and the close relatives P. muricata and P. attenuata are very susceptible, while pines of subsection Oocarpa were extremely resistant. Within P. radiata, variation in susceptibility has been observed in California populations of both planted and naturally regenerated trees (Storer et al., 1999, 2002), and similar variation is found among susceptible pine species from the southern USA: P. elliottii (Dwinell & Phelps, 1977) P. taeda and P. virginiana (Kelley & Williams, 1982; Kuhlman et al., 1982; Barrows-Broaddus & Dwinell, 1984). Based on lab tests, P. echinata and P. virginiana native to the Eastern USA are rather susceptible to the pathogen (Kim et al. 2008). The Mexican Pinus patula, widely used in South Africa is extremely susceptible, but other pine species from Mexico and their hybrids with P. patula are much less so (Mitchell et al. 2012). 

If individual valuable amenity trees are affected, pruning with appropriate hygienic precautions can restore the value of the tree. In the case of isolated infected trees in an otherwise pest-free area, it may be more appropriate to remove and destroy the tree. In general, in affected areas, it is preferable to use trees other than Pinus, or less susceptible Pinus spp., in amenity plantings. For example, in California, several exotic pine species that are suitable for a Mediterranean climate and less susceptible than the native species (Gordon et al., 1998a,b) have been (should be? could be?) used.

Phytosanitary risk

F. circinatum has shown its capacity to spread to new areas on pine seedlings (California, Mexico, South Africa, Chile, Spain, Portugal, Japan). It could readily be further spread by international movement of infected Pinus seeds and seedlings. However, it could also be moved by international trade of non-pine seedlings as it has occurred for Douglas-fir (Vogler et al. 2004). In addition to pathogen sources outside the EPPO region, it should be clearly stated that the pathogen is also present within the EPPO region, and that these outbreaks represent a possible source for further movement of the pathogen within the EPPO region. The pathogen in fact was first reported in Asturias, Spai (Landeras et al., 2005) and it has subsequently become established in restricted areas of northern Spain and Portugal (Iturritxa et 2013, Bragança et al., 2009; EPPO, 2019). There have also been occurrences of F. circinatum in France and Italy, now reportedly eradicated (EPPO, online). The areas to which it has spread have Mediterranean-type climates, so that, within the EPPO region, the Mediterranean area is clearly at risk since Pinus spp. are widely planted there.  However, oceanic warm regions such as the entire West Coast of the Iberian Peninsula, of France and of the British Isles and Ireland may also be at risk.

Pitch pine canker probably presents most danger to forest nurseries. Damage to plantations or native forests seem more likely to arise in cool and humid regions of Europe or in Mediterranean regions.


Quarantine regulations are crucial to minimize the risk of new introductions into disease-free countries. Seed lots should be tested using molecular methods already developed for F. circinatum.  The cryptic presence of F. circinatum in pine seedlings or herbaceous plants (Hernandez-Escribano et al., 2018b) could increase the risk of non-detection of infected material in pine nurseries which could lead to spread of the disease in the nursery and to forests and, consequently, increase the management costs (Vettraino et al., 2018). Breeding for resistance appears to be the best option for control in the field (Martin-Garcia et al., 2019) and other measures may be integrated for Pitch Canker control.

Since the first reported outbreaks of F. circinatum in 2005 in Spain, specific emergency measures were adopted to prevent the introduction into and the spread of F. circinatum within the EU. The emergency measures indicate that the Member States shall conduct annual surveys for the presence of F. circinatum. These surveys should consist of visual examinations and if there is any suspicion of infection, the collection of samples and performance of tests. The emergency measures also enforce special requirements for the import and internal movement of some of the host plants and plant products of F. circinatum (EFSA 2020).

Seeds of Pinus sp. imported from countries where F. circinatum is present should be free from the pest. Seed-testing methods are presented by Anderson (1986), Correll et al. (1991) and ISTA (2020). There is a certain risk of introduction with soil but, in general, most EPPO countries prohibit the import of soil, and restrict the import of plants with soil (EPPO, 1994), from other continents. These measures should be effective against F. circinatum. Host plants for planting should be free from the pest. Seed and plants of other confirmed hosts from countries where the pest is present, in particular Douglas-fir should be screened as well, based on the precedent of an infected Douglas-fir seedling resulting in intercontinental movement of the pathogen (Vogler et al., 2004).

Based on the experience in California, the discovery of infections in nurseries and/or in forest stands should trigger a whole suite of phytosanitary measures. In plant nurseries, the following should be implemented: soil exposed to inoculum should be pasteurized, growing containers should be sterilized, infected plants and plants within the same lot should be culled and autoclaved, raised planting beds and walkways should be disinfected. In forest stands, wood and foliage from cut trees should be burned or piled locally and not moved to different sites, while tools and equipment should be sterilized at the end of operations in each infected site. Approaches employed for sterilization, disinfection or sanitation of equipment/soil and destruction of infected plant material approaches may vary, as long as proven effective (Vettraino et al., 2018).

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This datasheet was extensively revised in 2021 by Matteo Garbelotto (University of California – Berkeley, USA) and Margarita Elvira-Recuenco (Forest Research Centre of the National Institute for Agricultural and Food Research and Technology INIA, Spain). Their valuable contribution is gratefully acknowledged.

How to cite this datasheet?

EPPO (2024) Fusarium circinatum. EPPO datasheets on pests recommended for regulation. https://gd.eppo.int (accessed 2024-02-21)

Datasheet history 2021-01-15

This datasheet was first published in the EPPO Bulletin in 2005 and revised in 2021. It is now maintained in an electronic format in the EPPO Global Database. The sections on 'Identity', ‘Hosts’, and 'Geographical distribution' are automatically updated from the database. For other sections, the date of last revision is indicated on the right.

EPPO (2005) Data sheets on quarantine pests. Gibberella circinata. EPPO Bulletin 35(3), 383–386. https://doi.org/10.1111/j.1365-2338.2005.00905.x