First report of leaf blight caused by Phytophthora ramorum on periwinkle (Vinca minor) in Washington State, USA.

Phytophthora ramorum (Werres, De Cock & Man in't Veld) was recovered from symptomatic foliage of periwinkle at a botanical garden in WA in March 2015. Symptoms were tan colored lesions with a dark brown margin visible on both surfaces of the leaf and were found on wounds or around leaf margins. Periwinkle is native to Europe and is commonly used for ground cover in ornamental landscapes. It is known to be invasive in US forests near the urban/wildland interface. Potential spread of P. ramorum into WA forests is of regulatory concern, as well as long distance spread to other states via nursery stock (7 CFR §301.92-2). Phytophthora ramorum was isolated from symptomatic foliage by excising leaf pieces 4-6 mm in diameter and surface-sterilizing in 0.6% sodium hypochlorite followed by two rinses in sterile water. Leaf pieces were plated on PARP medium (Ferguson and Jeffers 1999) and after 2-3 days at 20°C, slow-growing dense colonies with coralloid hyphae were isolated onto V8 agar. Colony morphology and chlamydospore production were consistent with descriptions of P. ramorum (Werres et al. 2001), except that the isolate was slower growing and had irregular, non-wildtype morphology (Elliott et al. 2018) compared to other isolates of P. ramorum. ITS and COX1 regions of mycelial DNA was amplified and sequenced to confirm the identity of P. ramorum using primers ITS1/ITS4 (White et al. 1990) and COX1F1/COX1R1 (Van Poucke et al. 2012). Sequences were submitted to GenBank (accession nos. ITS MT031975, COX1 MT031974). BLAST results showed at least 98% similarity with sequences of P. ramorum (ITS, MN540640 [98%]; COX1, EU124920 [100%]), and belonged to the NA1 clonal lineage. Pathogenicity of P. ramorum to periwinkle was confirmed by completing Koch's Postulates. Inoculum was grown on V8 agar plates at 20°C for two weeks until sporangia were abundant. A zoospore suspension was produced by flooding plates with 7 ml sterile water, incubating for 2 hours at 5°C, then for an additional hour at 24°C. Zoospores were observed under the microscope and quantified with a hemocytometer, then diluted to 2 x 105 zoospores/ml. A 10 µl droplet of inoculum was placed at one wounded and one unwounded site on six leaves on each of four plants. In addition, a set of four plants was inoculated by dipping foliage on one branch per plant into the zoospore suspension for 30 seconds. A set of four control plants were mock inoculated in the same manner using sterile water. The trial was repeated once. Inoculated plant materials were incubated in a moist chamber for 3-5 days and free moisture was present on foliage upon removal. Plants were held in a biocontainment chamber (USDA-APHIS permit # 65857) at 20C and symptom development assessed after 7 days (Figure S1). . Symptoms developed on foliage inoculated using both methods in both trials. Phytophthora ramorum was isolated once from droplet inoculated foliage at a wounded site on one plant. Reisolation onto PARP and then V8 agar was conducted from surface-sterilized symptomatic tissue and the presence of P. ramorum confirmed by observation of colony morphology and chlamydospore production. The presence of P. ramorum was also confirmed with DNA extraction from symptomatic foliage from plants from each of the two trials followed by PCR and sequencing of the COX1 gene (EU124920, 100%) (Figure S2). None of the water-inoculated controls were positive for P. ramorum. Low isolation success could be attributed to reduced pathogenicity due to being a non-wildtype isolate. Acknowledgements This work was supported by the USDA National Institute of Food and Agriculture, McIntire-Stennis project 1019284 and USDA APHIS Cooperative Agreement AP17PPQS&T00C070.

First report of leaf blight caused by Phytophthora ramorum on cherry laurel (Prunus laurocerasus) in Washington State, USA.

In April 2014, Phytophthora ramorum (Werres, De Cock & Man in't Veld) was recovered from symptomatic foliage of cherry laurel (Prunus laurocerasus) at an ornamental plant nursery in Washington State. Cherry laurel, also known as English laurel, is widely propagated in WA because it is commonly used in landscaping. It is invasive in forests near the urban/wildland interface in the western US and in Europe (Rusterholz et al. 2018). Given its popularity as an ornamental species, the potential of this host to spread P. ramorum is of regulatory concern due to possible long distance spread to other states via nursery stock. Foliar symptoms consisted of dark brown lesions near wounds or around leaf margins where water collected. Shot-hole symptoms characterized by abscission zones and dropping of infected tissues were also observed. Lesions expanded beyond the margin of the shot-hole in some cases (Figure S1A). Phytophthora was isolated from symptomatic foliage by surface-sterilizing leaf pieces in 0.6% sodium hypochlorite and 2 rinses in sterile water. They were plated on PARP medium (Ferguson and Jeffers 1999). After 2-3 days, a slow-growing dense colony with coralloid hyphae was isolated onto V8 agar. P. ramorum was identified by observing morphological features (Figure S1B). Colony and spore morphology matched that of P. ramorum (Werres et al. 2001). The isolate was confirmed as P. ramorum by PCR and sequencing of ITS and COX1 regions using primers ITS1/ITS4 (White et al. 1990) and COX1F1/COX1R1 (Van Poucke et al. 2012). Sequences were submitted to GenBank (accession nos. ITS MT031969, COX1 MT031968). BLAST results showed at least 99% similarity with sequences of P. ramorum (ITS, KJ755124 [100%]; COX1, EU124926 [99%]). Multilocus genotyping with microsatellite markers placed the isolate in the EU1 clonal lineage. Pathogenicity of P. ramorum on cherry laurel was confirmed by completing Koch's Postulates using the isolate taken from this host. Two trials were done in a biocontainment chamber (USDA-APHIS permit # 65857) since P. ramorum is a quarantine pathogen and greenhouse trials could not be conducted, using detached stems from mature, visibly healthy cherry laurel plants growing in a landscape. Phytophthora ramorum inoculum was grown on V8A plates at 20®C for 2 weeks until sporangia were abundant. A zoospore suspension was produced by flooding plates with 7 ml sterile water, incubating for 2 hours at 5®C, then 1 hour at 24®C. Zoospores were observed with light microscopy, quantified with a hemocytometer and diluted to 1 x 104 zoospores/ml. A 10 µl droplet was placed at 3 wounded and 3 unwounded sites on 4 leaves per branch. In addition, a set of samples was inoculated by dipping foliage into the zoospore suspension for 30 seconds. A set of controls was mock inoculated using sterile water. Four branches per inoculation treatment were used and the trial was repeated once. Inoculated plant materials were incubated in moist chambers for 3-5 days at 20®C. Free moisture was present on foliage upon removal. Symptom development was assessed after incubation in the biocontainment chamber at 20®C for 7 days (Figure S1C). Phytophthora ramorum was reisolated from symptomatic tissue and the recovered culture was verified morphologically and by PCR and sequencing. It was isolated more often from foliage dipped in zoospore suspension than droplet inoculated, and more from wounded than unwounded sites. None of the water-inoculated controls were positive for P. ramorum. The presence of P. ramorum was also confirmed with DNA extraction from surface-sterilized symptomatic foliage followed by PCR and sequencing of the COX1 gene (EU124926, 100%) (Figure S2). To our knowledge, this is the first report of P. ramorum naturally infecting cherry laurel in the United States. Acknowledgements This work was supported by the USDA National Institute of Food and Agriculture, McIntire-Stennis project 1019284 and USDA APHIS Cooperative Agreement AP17PPQS&T00C070 Literature cited Ferguson and Jeffers, 1999. Plant Disease 83:1129-1136 Van Poucke, K. et al. 2012. Fungal Biology 116: 1178-1191. http://dx.doi.org/10.1016/j.funbio.2012.09.003 Werres, S. et al. 2001. Mycol. Res. 105:1155-1165. White, T. J., et al. 1990. Page 315 in: PCR Protocols: A Guide to Methods and Applications. Academic Press, San Diego, CA.

Comparison of Five Detection and Quantification Methods for Phytophthora ramorum in Stream and Irrigation Water.

Propagules of Phytophthora ramorum, the causal agent of sudden oak death (SOD) and ramorum blight, can be recovered from infested stream and nursery irrigation runoff using baiting and filtration methods. Five detection methods, including pear and rhododendron leaf baits, Bottle O' Bait, filtration, and quantitative polymerase chain reaction (qPCR) performed on zoospores trapped on a filter were compared simultaneously in laboratory assays using lab or creek water spiked with known quantities of P. ramorum zoospores. The detection threshold for each method was determined and methods that could be used to quantify zoospore inoculum were identified. Filtration and qPCR were the most sensitive at detecting low levels of zoospores, followed by wounded rhododendron leaves, rhododendron leaf disks, and pear baits. Filtration, qPCR, and leaf disks were able to quantify P. ramorum zoospores ranging from 2 to 451 direct-plate CFU/liter while wounded leaves and pear baits appeared to be better at detection rather than quantification. The ability to detect and quantify P. ramorum inoculum in water will assist scientists, regulatory agencies, and nursery personnel in assessing the risk of spreading P. ramorum in nurseries and landscape sites where untreated infested water is used for irrigation.

Metal stress and decreased tree growth in response to biosolids application in greenhouse seedlings and in situ Douglas-fir stands.

To assess physiological impacts of biosolids on trees, metal contaminants and phytochelatins were measured in Douglas-fir stands amended with biosolids in 1982. A subsequent greenhouse study compared these same soils to soils amended with fresh wastewater treatment plant biosolids. Biosolids-amended field soils had significantly higher organic matter, lower pH, and elevated metals even after 25 years. In the field study, no beneficial growth effects were detected in biosolids-amended stands and in the greenhouse study both fresh and historic biosolids amendments resulted in lower seedling growth rates. Phytochelatins - bioindicators of intracellular metal stress - were elevated in foliage of biosolids-amended stands, and significantly higher in roots of seedlings grown with fresh biosolids. These results demonstrate that biosolids amendments have short- and long-term negative effects that may counteract the expected tree growth benefits.