Global geographic distribution and host range of Dothistroma species: a comprehensive review

R. Drenkhan*, V. Tomešová-Haataja, S. Fraser, R. E. Bradshaw, P. Vahalík, M. S. Mullett, J. Martín-García, L. S. Bulman, M. J. Wingfield, T. Kirisits, T. L. Cech, S. Schmitz, R. Baden, K. Tubby, A. Brown, M. Georgieva, A. Woods, R. Ahumada, L. Jankovský, I. M. ThomsenK. Adamson, B. Marçais, M. Vuorinen, P. Tsopelas, A. Koltay, A. Halasz, N. La Porta, N. Anselmi, R. Kiesnere, S. Markovskaja, A. Kačergius, I. Papazova-Anakieva, M. Risteski, K. Sotirovski, J. Lazarević, H. Solheim, P. Boroń, H. Bragança, D. Chira, D. L. Musolin, A. V. Selikhovkin, T. S. Bulgakov, N. Keča, D. Karadžić, V. Galovic, P. Pap, M. Markovic, L. Poljakovic Pajnik, V. Vasic, E. Ondrušková, B. Piškur, D. Sadiković, J. J. Diez, A. Solla, H. Millberg, J. Stenlid, A. Angst, V. Queloz, A. Lehtijärvi, H. T. Doğmuş-Lehtijärvi, F. Oskay, K. Davydenko, V. Meshkova, D. Craig, S. Woodward, I. Barnes

*Corresponding author for this work

Research output: Contribution to journalReview articlepeer-review

85 Citations (Scopus)


Dothistroma needle blight (DNB) is one of the most important diseases of pine. Although its notoriety stems from Southern Hemisphere epidemics in Pinus radiata plantations, the disease has increased in prevalence and severity in areas of the Northern Hemisphere, including Europe, during the last two decades. This increase has largely been attributed to expanded planting of susceptible hosts, anthropogenic dispersal of the causative pathogens and changes in climate conducive to disease development. The last comprehensive review of DNB was published in 2004, with updates on geographic distribution and host species in 2009. Importantly, the recognition that two species, Dothistroma septosporum and D. pini, cause DNB emerged only relatively recently in 2004. These two species are morphologically very similar, and DNA-based techniques are needed to distinguish between them. Consequently, many records of host species affected or geographic location of DNB prior to 2004 are inconclusive or even misleading. The objectives of this review were (i) to provide a new database in which detailed records of DNB from 62 countries are collated; (ii) to chart the current global distribution of D. septosporum and D. pini; (iii) to list all known host species and to consider their susceptibility globally; (iv) to collate the published results of provenance trials; and (v) to consider the effects of site factors on disease incidence and severity. The review shows that DNB occurs in 76 countries, with D. septosporum confirmed to occur in 44 and D. pini in 13. There are now 109 documented Pinaceae host taxa for Dothistroma species, spanning six genera (Abies, Cedrus, Larix, Picea, Pinus and Pseudotsuga), with Pinus being the dominant host genus, accounting for 95 host taxa. The relative susceptibilities of these hosts to Dothistroma species are reported, providing a resource to inform species choice in forest planting. Country records show that most DNB outbreaks in Europe occur on Pinus nigra and its subspecies. It is anticipated that the collaborative work described in this review will both underpin a broader global research strategy to manage DNB in the future and provide a model for the study of other forest pathogens.

Original languageEnglish
Pages (from-to)408-442
Number of pages35
JournalForest Pathology
Issue number5
Early online date13 Sept 2016
Publication statusPublished - 1 Oct 2016

Bibliographical note


This study was partially supported by the EU COST Action FP1102 DIAROD (Determining Invasiveness and Risk of Dothistroma,, Norwegian Financial Mechanism 2009–2014 under the project EMP162 and the Institutional Research Funding IUT21-04. We would like to thank Angus Carnegie, Jim Walla and Tod Ramsfield for providing information regarding DNB in Australia, the USA and Canada, respectively, and four anonymous reviewers for valuable corrections and suggestions for the manuscript.


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