Effect of a protectant copper application on Psa infection of kiwifruit trap plants

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310 Effect of a protectant copper application on Psa infection of kiwifruit trap plants J.L. Tyson 1, S.J. Dobson 2 and M.A. Manning 1 1 The New Zealand Institute for Plant & Food Research Limited, Private Bag 92169, Auckland, 1142, New Zealand 2 The New Zealand Institute for Plant & Food Research Limited, 412 No. 1 Road, RD2, Te Puke, 3182, New Zealand Corresponding author: joy.tyson@plantandfood.co.nz Abstract Pseudomonas syringae pv. actinidiae (Psa) causes bacterial canker of kiwifruit, which is an ongoing threat to New Zealand kiwifruit production. Disease control depends on orchard practices such as removal of visibly diseased material, pruning during low-risk periods, and the application of foliar bactericides. Although the use of copper compounds on Actinidia species (kiwifruit) can cause phytotoxicity, copper-based formulations remain a key component of Psa control in New Zealand. The effect of single copper applications on Psa infection of Hort16A trap plants was studied over the Spring of 2014 (Sept Nov). Psa leaf spots were observed at the beginning of October, appearing first on the untreated plants. Although the copper sprays did not achieve complete protection, particularly as the inoculum built up during November, the copper-sprayed plants always had less disease than the untreated plants. Keywords Pseudomonas syringae pv. actinidiae, Actinidia chinensis var. chinensis Hort16A. INTRODUCTION Pseudomonas syringae pv. actinidiae (Psa) causes bacterial canker of kiwifruit, which is currently the most important disease of cultivated Actinidia species worldwide, and is an ongoing threat to New Zealand kiwifruit production (Tyson et al. 2016). Disease control depends on orchard practices such as removal of obviously diseased material, pruning during dry periods to minimise the potential inoculum load on susceptible wounds, and the strategic application of foliar bactericides (copper formulations, antibiotics and biologicals) to minimise infection. Although use of copper compounds on kiwifruit can cause phytotoxicity problems (Donati et al. 2014), copper-based formulations remain a key component of Psa control in New Zealand. Recent studies of Psa inoculum production and infection over extended periods (Beresford & Tyson 2014; Tyson et al. 2014) have shown that rainfall is essential for disease development on trap plants. There were also indications of a strong seasonal component to Psa epidemiology. Over the spring of 2013 (Sept, Oct, Nov), Psa leaf spots developed on the trap plants after every rain event. From late summer to late winter, disease development was more erratic (Tyson et al. unpub. data). During spring, kiwifruit vines break dormancy, with leaves emerging first, then blossoms. Young leaves are particularly susceptible to Psa (Tyson New Zealand Plant Protection 70: 310-314 (2017) www.nzpps.org

311 et al. 2015); the flower buds can also be affected by blossom blight, making this a key time for Psa control. This project aimed to study the effect of a copper application (Nordox) on Psa infection of trap plants over the spring of 2014 (Sept- Oct-Nov). MATERIALS AND METHODS From 8 September to 28 November 2014, trap plants were exposed for 4-day periods in two Psa-infected blocks (Blocks 40 and 50) of mature kiwifruit on the Te Puke Research Orchard (TPRO). Block 50 contained Actinidia chinensis var. deliciosa Hayward and block 40 contained a mixture of new and non-commercial varieties. Both blocks were known to have substantial amounts of Psa leaf spotting over the previous two years. Trap plants Tissue-cultured plantlets of A. chinensis var. chinensis Hort16A were grown in a glasshouse in a Psa-free area. At approximately 3 months post-tissue culture, the plants were 30 40 cm high and had 10 15 leaves. To obtain plants that were as uniform as possible, plants were tipped at a height of 40 cm. Within each experimental block, four sets of five plants were exposed for 96 h periods (09:00 Monday 09:00 Friday). Hanging containers were used to suspend the plants just below the canopy. Within each block, two sets of plants were untreated controls and two sets were sprayed with copper oxide (Nordox at 37.5 g/100 L), targeting both leaf surfaces, to run-off before being exposed to potential infection in the orchard. After 96-h exposure in the field, the plants were incubated in a laboratory under growth lights at c. 20 C for 21 days and then assessed for symptom expression (leaf spots). Any leaves that developed Psa-type leaf spots were sent to the Plant & Food Research Mt Albert Research Centre (MARC) for diagnosis. Assessment of phytotoxicity After 96-h exposure in the orchard and a further 21 days incubation, the trap plants were visually assessed for signs of phytotoxicity on the leaves. Psa isolation and identification Areas of leaf with disease symptoms were excised, macerated in 200 µl bacteriological saline (0.85% NaCl in sterile distilled water) and left for 5 min, after which 100 µl of the resulting suspension was spread across KBC, an agar medium semi-selective for Pseudomonas species (Mohan & Schaad 1987). The isolation plates were incubated at 20 C for 72 h and then assessed for bacterial growth. DNA extraction, and qpcr conditions and analysis, were as described by Tyson et al. (2012), using the primers PsaF3 and PsaR4 developed by Rees-George et al. (2010). In addition, bacterial 23S primers (Anthony et al. 2000) were used in qpcr as an internal control to check that the DNA was PCR-competent. In this study, a Cp (crossing point or threshold value) value below 30 was interpreted as a Psa positive result, 30 35 as a weak positive, and a Cp value above 35 as a negative result. Weather data Hourly temperature and rainfall data were collected from the weather station at TPRO over the period of trapping. The total amount of rainfall collected during each 96-h exposure period was then calculated. The weather data were downloaded from the National Institute of Water and Atmospheric Research Ltd (NIWA) National Climate Database (CliFlo) for the period of the trial (Te Puke Ews, station no. 12428, latitude 37.822, longitude 176.324). RESULTS No phytotoxicity was observed on any of the copper-treated trap plants during the trial. No Psa leaf spots developed on any coppertreated or untreated plants exposed during September 2014. The first Psa leaf spots were

312 observed at the beginning of October, appearing first on the untreated control plants (Table 1). Leaf spots were not observed on copper-treated plants until the end of October. The number of copper-treated plants with Psa leaf spots was always lower than for untreated plants so the copper treatment appeared to have a protective effect. Low levels of leaf spots observed at many of the sampling dates meant that statistical analysis of variation among the replicate sets of blocks was not meaningful. The amount of rainfall collected over each 96-h exposure period is shown in Figure 1 along with the percentage of plant with Psa leaf spots observed for either untreated or copper-treated plants. DISCUSSION In this trial, copper-treated and untreated control trap plants of the highly susceptible kiwifruit cultivar Hort16A were exposed to natural Psa inoculum in an infected orchard over 12 weeks in September, October and November 2014, which is the New Zealand spring. Infection of kiwifruit plants by Psa is known to be affected by leaf age (Tyson et al. 2015), with young leaves being more susceptible to the bacterium, making spring a crucial period for disease control. Throughout the spring of 2014, the coppertreated trap plants always had less disease than the untreated plants. However, the copper treatment did not completely protect the plants from Psa, particularly as Psa inoculum built up in the orchard blocks during November. Psa leaf spots developed after 7 of the 12 weeks of the trial, always after periods of rain. No spots developed after the single exposure period during which there was no rainfall. This result is consistent with the results of previous Table 1 The number of Actinidia chinensis var. chinensis Hort16A trap plants with Pseudomonas syringae pv. actinidiae (Psa) leaf spots from 12 sets of 40 plants, either treated with copper oxide or left untreated, 21 d after exposure in an infected orchard for 96-h periods during spring 2014. Date exposed Cumulative rain (mm over the 96-h exposure period) Number of plants with Psa leaf spots Copper treated (n=20) Untreated (n=20) Reduction in Psa after application of copper oxide (%) 8-Sep-14 16.7 0 0 - Crop growth stage 15-Sep-14 23.4 0 0 - budburst 22-Sep-14 4.1 0 0-29-Sep-14 3.4 0 0 - budburst 6-Oct-14 1.8 0 1 100 13-Oct-14 0.0 0 0 - budburst 20-Oct-14 0.3 0 1 100 28-Oct-14 9.9 0 7 100 leaves 3-Nov-14 10.3 9 11 18 10-Nov-14 4.7 1 7 86 leaves, flowers 17-Nov-14 17.2 5 16 69 24-Nov-14 0.9 0 3 100 leaves, flowers

313 Figure 1 Actinidia chinensis var. chinensis Hort16A trap plants, either treated with copper oxide or left untreated, with Pseudomonas syringae pv. actinidiae (Psa) leaf spots after exposure in an infected orchard for 4-day periods during spring 2014. studies that have shown that leaf infection is dependent on rainfall (Tyson et al. 2014; Beresford et al. 2017). The two major instances where the coppertreated plants were not fully protected by copper applications were marked by periods of high inoculum availability, as indicated by the increased incidence of disease on the untreated control plants and increasing amounts of leaf spotting in the mature kiwifruit plants. The fact that some leaf spots were found on copper-treated plants is an important issue of concern to the kiwifruit industry. Strains of Psa with copper-resistance were detected as early as 1987 in Japan (Nakajima et al. 2002) and in New Zealand isolates of Psa in 2014 (Colombi et al. 2017), 4 years after the first detection of kiwifruit canker in 2010 (Everett et al. 2011). The strain of Psa causing leaf spotting on the coppertreated plants was not tested for resistance to copper, however, and there was no indication that there was resistance to copper in the orchard being studied. ACKNOWLEDGEMENTS The authors would like to thank S.G. Casonato for applying the copper applications each week, and C. Middleditch for technical help. This work was partially funded by the Plant and Food Research Kiwifruit Reinvestment Fund (KRIP). REFERENCES Anthony RM, Brown TJ, French GL 2000. Rapid diagnosis of bacteremia by universal amplification of 23S ribosomal DNA followed by hybridization to oligonucleotide array. Journal of Clinical Microbiology 38(2): 781-788.

314 Beresford RM, Tyson JL 2014 Seasonal accuracy of the Psa risk model. New Zealand Kiwifruit Journal: 18-19. Beresford RM, Tyson JL, Henshall WR 2017. Development and validation of an infection risk model for bacterial canker of kiwifruit using a multiplication and dispersal concept for forecasting bacterial diseases. Phytopathology 107(2): 184-191. Colombi E, Straub C, Künzel S, Templeton MD, McCann HC, Rainey PB 2017. Evolution of copper resistance in the kiwifruit pathogen Pseudomonas syringae pv. actinidiae through acquisition of integrative conjugative elements and plasmids. Environmental Microbiology 19(2): 819-832. Donati I, Buriani G, Cellini A, Mauri S, Costa G, Spinelli F 2014. New insights on the bacterial canker of kiwifruit (Pseudomonas syringae pv. actinidiae). Journal of Berry Research 4: 53-67. Everett KR, Taylor RK, Romberg MK, Rees- George J, Fullerton RA, Vanneste JL, Manning MA 2011. First report of Pseudomonas syringae pv. actinidiae causing kiwifruit bacterial canker in New Zealand. Australasian Plant Disease Notes 6: 67-71. Mohan SK, Schaad NW 1987. An improved agar plating assay for detecting Pseudomonas syringae pv. syringae and P. s. pv. phaseolicola in contaminated bean seed. Phytopathology 77(10): 1390-1395. Nakajima M, Goto M, Hibi T 2002. Similarity between copper resistance genes from Pseudomonas syringae pv. actinidiae and P. syringae pv. tomato. Journal of General Plant Pathology 68(1): 68-74. Rees-George J, Vanneste JL, Cornish DA, Pushparajah IPS, Yu J, Templeton MD, Everett KR 2010. Detection of Pseudomonas syringae pv. actinidiae using polymerase chain reaction (PCR) primers based on the 16S-23S rdna intertranscribed spacer region and comparison with PCR primers based on other gene regions. Plant Pathology 59(3): 453-464. Tyson JL, Rees-George J, Curtis CL, Manning MA, Fullerton RA 2012. Survival of Pseudomonas syringae pv. actinidiae on the orchard floor over winter. New Zealand Plant Protection 65: 25-28. Tyson JL, Horner IJ, Curtis CL, Blackmore A, Manning MA 2015. Influence of leaf age on infection of Actinidia species by Pseudomonas syringae pv. actinidiae. New Zealand Plant Protection 68: 328-331. Tyson JL, Curtis CL, Manning MA, Dobson SJ, McKenna CE 2016. Preliminary investigations of the risk of plant debris as a Pseudomonas syringae pv. actinidiae inoculum source. New Zealand Plant Protection 69: 11-16. Tyson JL, Manning MA, Curtis CL, Dobson SJ, McKenna CE, Vergara MJ 2014. Inoculum production and infection of kiwifruit plants by Pseudomonas syringae pv. actinidiae in New Zealand. VIII International Symposium on Kiwifruit. Pp. 105.