First report of Diplodia tip blight on Scots pine in Finland
Terhonen E. (2023). First report of Diplodia tip blight on Scots pine in Finland. Silva Fennica vol. 56 no. 4 article id 22008. https://doi.org/10.14214/sf.22008
Diplodia sapinea (Fr.) Fuckel causes shoot blight on Scots pine (Pinus sylvestris L.). This fungus has been discovered in Finland as a saprophyte in 2015 on Scots pine cones. The endophytic mode of this fungus was later discovered in healthy Scots pine twigs. In 2021 the disease, Diplodia tip blight was observed on Scots pine in Finland. Currently, the disease symptoms are poorly identified so the role of D. sapinea in disease outbreaks in Finland are easily overlooked. The identification of the fungi is challenging in field conditions and requires targeted identification in laboratory. In this research note I report the first Diplodia tip blight outbreaks observed in Finland, the typical disease symptoms, and methodology for the species identification. Samples were collected from symptomatic trees based on observations made by the citizens. Diplodia sapinea was isolated from defoliated and surface sterilized twigs. The species identification by morphological characters was further confirmed with sequencing of ITS region of rDNA and with species-specific primers. A pathogenicity test confirmed that D. sapinea was the disease agent causing shoot blight. This is the first report of Diplodia tip blight on Scots pine in Finland.
Pinus sylvestris; drought; Diplodia sapinea; Sphaeropsis sapinea; emerging fungal disease
Received 30 September 2022 Accepted 11 January 2023 Published 23 January 2023
Available at https://doi.org/10.14214/sf.22008 | Download PDF
Diplodia tip blight is a shoot blight disease of Scots pine (Pinus sylvestris L.), caused by ascomycete Diplodia sapinea (Fr.) Fuckel. Diplodia sapinea is present in its host as dormant saprotroph (Müller et al. 2019) or asymptomatic endophyte (Terhonen et al. 2021). Due to additional biotic stressors (e.g. drought) that the host encounters (Blumenstein et al. 2021a, 2022), D. sapinea can switch its lifestyle to pathogenic, leading to unexpected disease (Diplodia tip blight) outbreaks on Scots pine in the field and nurseries (Brodde et al. 2019; Blumenstein et al. 2021b; Larsson et al. 2021; Oliva et al. 2021). Scots pine is the most common forestry species in Finland with a volume of 1250 million cubic meters, corresponding to 50% of the growing stock (Mäkisara et al. 2022). As conifers are long living organisms, they might not be able to locally adapt to the rapid changes in climate and environment. This may make Scots pine more prone to drought stress that can lead to higher disease outbreaks due to D. sapinea (Brodde et al. 2019).
Diplodia sapinea was first recorded on cones in southern Finland in 2015 (Müller et al. 2019). In 2019 it was found as endophyte from healthy Scots pine twigs collected in southern Finland (Terhonen et al. 2021). In autumn 2021 and spring 2022, first blighted shoots of Scots pine were observed in several locations in coastal Finland. The symptoms resembled D. sapinea causing the disease Diplodia tip blight. Diplodia sapinea can be assumed to be a new pathogen on Scots pine in Finland. Previously, it has been recorded only as a harmless endophyte or dormant saphrophyte in Finland, but various stressors of the host tree might promote the launch to pathogenic mode. The aim of this research note is to show the disease symptoms in the field, raise awareness and develop pipeline to correctly identify D. sapinea in the laboratory.
Declining shoots (7) were collected from either seedlings (Fig. 1A), saplings (15-year-old trees) (Fig. 1B, C) or mature trees (Fig. 2A, B) in five different Finnish locations (Table 1). The branches were defoliated, sprayed with 70% EtOH, air dried and surface sterilized 1 min in 2.4% NaOCl. Thereafter, twigs were gently scraped to show the borderline of healthy and necrotic tissue and cut into pieces (~5 mm segments). The segments (containing bark, phloem, and sapwood) were plated on modified malt yeast peptone agar (MYP) (Langer 1994; Bußkamp et al. 2020). Maximum five twig segments were placed on MYP medium and incubated at room temperature and daylight. Emerging mycelia could be easily morphologically identified as D. sapinea. The hyphae are downy, turning from white to greenish/grey/black in few days. Representative D. sapinea strains are stored on MYP slants at 4 °C at Natural Resources Institute Finland (Luke).
|Table 1. Site locations in Finland, sequence ID in GeneBank and necrosis length of the representative Diplodia sapinea strains.|
|Location||Tree age status||Sequence ID in NCBI||Inoculation experiment, arithmetic necrosis length (cm)|
|* 15-year-old Scots pines|
The DNA were isolated from presentative strains (Table 1) by using PrepMan™ Ultra Sample preparation reagent (Applied Biosystems, Foster City, CA, USA) (Linnakoski et al. 2016). The ITS1-5.8S-ITS2 region of rDNA was amplified using primer pair ITS1-F (White et al. 1990) and ITS4 (Gardes and Bruns 1993). Briefly, PCR protocol was as follows: Dream Tag green mix (2X) (Thermo Scientific™), 200 µM dNTP, 0.5 µM primer 1, 0.5 µM primer 2, 1 µl of crude template DNA; the reaction was adjusted to 15 µl with autoclaved MQ H2O. PCR conditions used were 94 °C for 3 min; 30 cycles of 94 °C for 30 s, 55 °C for 1 min, 72 °C for 1 min, and 72 °C for 10 min. Amplifications were confirmed on a 1.5% agarose gel (Ethidium Bromide staining), and the visual detection was made by ultraviolet transillumination. Samples were purified using the EXO-SAP (Exonuclease I–Shrimp Alkaline Phosphatase, Thermo Fisher Scientific, Waltham, MA, USA) protocol (Linnakoski et al. 2016) and sequenced using the ITS1 primer at Microsynth SEQLAB (Germany).
The D. sapinea ITS sequences are deposited in GenBank with accession numbers OP103742-OP103748 (Table 1). The species-specific primers DiSapi-F (3´- CCCTTATATATCAAACTATGCTTTGT-5´) (Adamson et al. 2021) and Diplo-R (3´-TTACATAGAGGATTGCCTTCG-5´) (Adamson et al. 2021) confirmed the species identification. PCR protocol was 0.2 U/µl DNA polymerase (DreamTaq DNA Polymerase, Thermo Scientific™), 1X PCR Buffer, 200 µM dNTP, 0.5 µM primer 1, 0.5 µM primer 2, 10 µl of crude DNA (diluted to 1:50 from the original extracted concentration), and finally the reaction was adjusted to 25 µl with MQ H2O. PCR conditions were 95 °C for 5 min, 35 cycles of 95 °C for 30 s, 55 °C for 30 s, 72 °C for 1 min, and 72 °C for 10 min (Adamson et al. 2021). Sterile MQ H2O were used as negative control. The correct species (D. sapinea) was determined by the visual detection (the formed band with a size of 500 bp) made by ultraviolet transillumination of DNA amplicons on a 1.5% agarose gel (1 hour, 120V) (Adamson et al. 2021).
In June 2022 one-year-old Scots pine seedlings were inoculated with seven D. sapinea strains (Table 1) as described in Blumenstein et al. (2021a, see Fig. 3). The terminal shoot growth length had ended, and terminal bud had developed. Briefly, mycelial plugs (5 mm diameter) were taken from a seven-day-old culture growing on malt yeast peptone (MYP) plates. The terminal bud of each seedling (three seedlings per strain) was cut (~0.2 cm) with scissors and the mycelial plug placed on the exposed area. The inoculated shoots were then wrapped with Parafilm® for seven days. Seedlings were kept outside for seven weeks and watered when needed. The observed symptoms were similar to those seen in the field (Fig. 3a). Each shoot inoculated with D. sapinea showed symptoms of the disease: browning of the shoots and death of the needles. Necrosis in phloem and sapwood was measured and D. sapinea was reisolated from infected parts as described above. The three control shoots, inoculated with MYP plugs, remained healthy (Fig. 3b) and attempts to isolate D. sapinea were made.
Data were analysed using the R, version 3.5.1. (R Core Team, 2019). A generalized linear model was constructed to evaluate the fixed effects of strain, seedling height and number of side shoots on the length of the necrosis. Differences were considered significant if p-value ≤ 0.05.
The symptoms of Diplodia tip blight were seen from July onwards (Fig. 1–3). Brown shoots (current-year growth) were declining towards the late summer (July–August), and they looked like drought symptoms. Similarly, needles turned brown from the base as the phloem died, and needles either shed or stayed attached to the shoot until spring (Fig. 1, 2). The blighted shoots could be observed until the following spring (Fig. 1, 2). The disease development in one shoot can easily be followed during the summer (browning of the needles and shoot, Fig. 1A).
Diplodia sapinea was isolated on the borderline of the living and dead phloem and sapwood. The inoculation of presentative strains to Scots pine seedlings lead to typical symptoms of Diplodia tip blight (Fig. 3). TheKoch’s Postulates 2–4 were fulfilled for the putative causal agent D. sapinea because: (2) D. sapinea was the most commonly isolated fungi from the diseased Scots pine; (3) Inoculation of a healthy Scots pine with D. sapinea caused the disease; (4) D. sapinea was re-isolated from the inoculated, diseased Scots pine.
The blighted shoots observed in the field (Fig. 1, 2) were dying due to D. sapinea. No significant difference in the necrosis in the shoot was observed, based on the strain (p = 0.0912), seedling height (p = 0.819), or number of side shoot (p = 0.283). Necrosis varied between the strains (Table 1) and were much higher than in control plants (arithmetic length 0.1 cm). However, due to the high variation and low sample number no statistical differences were observed in the data.
This is the first report of Diplodia tip blight on Scots pine in Finland. The first symptoms were observed in autumn 2021 and after release of the bulletin by Luke (Luke, 15.11.2021) the information reached several forest owners. The number of the contacts from forest owners concerning the disease symptoms after March 2021 showed that this disease might be more common (E. Terhonen, personal observation) than previously thought. Here I report only the very first findings. The disease agent, D. sapinea, has been earlier found in Finland from cones (Müller et al. 2019) and from healthy twigs as an endophyte (Terhonen et al. 2021). Diplodia sapinea can turn from harmless to pathogenic causing Diplodia tip blight in stressed trees. The stress can be consequence from changes in environment (drought, temperature) (Oliva et al. 2021; Blumenstein et al. 2022) or related to biotic damage, e.g. Heterobasidion annosum s.s. (Fr.) Bref. disturbing the water supply (Dr. Gitta Langer, NW-FVA, pers. obs.). Diplodia sapinea is a previously unknown, most likely opportunistic, Scots pine pathogen in Finland, and the disease Diplodia tip blight has potential to increase in the near future (Brodde et al. 2019). Symptoms can be identified in late summer, however, the confirmation for the fungal species still requires DNA based identification. The protocol presented in this research note can be shortened, e.g. DNA can be extracted from the phloem (preferably including also sapwood), followed by the species-specific primer identification (Adamson et al. 2021). The culture-based method using MYP was adapted from Buβkamp et al. (2020), used routinely to isolate D. sapinea in Germany. For the isolation studies, I recommend using MYP media over the commonly used 1.5% MEA (Malt Extract Agar) or PDA (Potato Dextrose Agar). The texture, growth rate and colour of this fungi differ between these medias, and MYP results easiest morphological identification. Our aim in Luke is to collect D. sapinea strains from all the areas where the typical disease has been observed. For this Luke continues to collect observations and samples from citizens of Finland.
The research material is available from the author on reasonable request.
This study was funded by Alfred Kordelin Foundation.
The author would like to thank Katri Leino, Tuija Hytönen and Dr. Suvi Sutela for their excellent assistance in laboratory and in the field. Professor Jarkko Hantula is acknowledged for his support.
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