Source: OREGON STATE UNIVERSITY submitted to NRP
UNDERSTANDING HOST JUMPS: EVALUATING THE RISK OF PHYTOPHTORA PLUVIALIS TO WESTERN HEMLOCK IN THE USA
Sponsoring Institution
National Institute of Food and Agriculture
Project Status
ACTIVE
Funding Source
Reporting Frequency
Annual
Accession No.
1032412
Grant No.
2024-67013-42452
Cumulative Award Amt.
$682,500.00
Proposal No.
2023-10116
Multistate No.
(N/A)
Project Start Date
Jun 1, 2024
Project End Date
May 31, 2027
Grant Year
2024
Program Code
[A1112]- Pests and Beneficial Species in Agricultural Production Systems
Recipient Organization
OREGON STATE UNIVERSITY
(N/A)
CORVALLIS,OR 97331
Performing Department
(N/A)
Non Technical Summary
Global trade and climate change accelerate and compound the emergence of plant pathogens and impacts on natural and managed ecosystems. Phytophthora pluvialis is a foliar pathogen of conifer trees that has repeatedly emerged in the United States (US) and invaded New Zealand (NZ) and more recently the United Kingdom (UK). Its emergence has caused severe epidemics on economically important conifer trees in both plantations and wild land forests. In its most recent emergence, P. pluvialis not only jumped to a new host but was associated with a devastating shift in disease etiology. Studying P. pluvialis is of direct relevance in support of goals to improve the long-term sustainability and competitiveness of U.S. agricultural systems. The change in disease etiology is of particular concern. Its potential effects on the forest industry in the Pacific Northwest of the US are significant. Western hemlock and Douglas-fir, the two main hosts of this pathogen, make up most of the crop trees planted on the 8.1 million acres of private industrial forest land. We aim to: 1) Characterize the variation in suscpetibility to P. pluvialis within and among populations of Douglas-fir and western hemlock; 2) use phylogeny guided phenotyping of pathogen populations; and 3) develop and deploy a multiplex CRISPR based SHERLOCK assay to detect major lineages of P. pluvialis in the field. These aims will allow us to evaluate and attenuate the risk of P. pluvialis to western hemlock and Douglas-fir forests in the USA.
Animal Health Component
50%
Research Effort Categories
Basic
50%
Applied
50%
Developmental
(N/A)
Classification

Knowledge Area (KA)Subject of Investigation (SOI)Field of Science (FOS)Percent
1230612116050%
1230612117025%
2020612108025%
Goals / Objectives
Global trade and climate change accelerate and compound the emergence of plant pathogens and impacts on natural and managed ecosystems. Phytophthora pluvialis is a foliar pathogen of conifer trees that has repeatedly emerged in the United States (US) and invaded New Zealand (NZ) and more recently the United Kingdom (UK). Its emergence has caused severe epidemics on economically important conifer trees in both plantations and wildland forests. In its most recent emergence, P. pluvialis not only jumped to a new host but was associated with a devastating shift in disease etiology. In addition to infecting foliage, the pathogen infected the main stem of trees and caused cankers that led to tree mortality (Fig. 1). This change in disease etiology is of particular concern because of potential effects on the forest industry in the Pacific Northwest of the US. In this region western hemlock and Douglas-fir, the two main hosts of this pathogen, make up most of the crop trees planted on the 8.1 million acres of private industrial forest land. Testing the following specific hypotheses is essential for determining impacts of emergence by P. pluvialis on the US forest industrySpecific hypothesis 1: The invasion in the UK by P. pluvialis is the result of a genetic bottleneck of the host followed by accidental selection of susceptible western hemlock genotypes.Specific hypothesis 2: The shift in disease etiology is the result of emergence of a new clade of P. pluvialis able to infect hemlock and cause stem cankers.Specific hypothesis 3: Differences in environmental conditions among locations explain changes in the etiology of the disease and host shifts by P. pluvialis.The Objectives of this proposal are:Characterize the variation in susceptibility to P. pluvialis within and among populations of Douglas-fir and western hemlock.Genotype western hemlock and Douglas-fir populations from the US and the UK.Evaluate differences in susceptibility of leaves and stem tissue among populations of western hemlock and Douglas-fir.Evaluate the epidemiological risk to western hemlock and Douglas-fir tree farms in the USA.Evaluate growth and sporulation potential of representative P. pluvialis isolates across a range of temperatures and on inoculated seedlings.Contrast infection biology on Douglas-fir and western hemlock.Develop and deploy a multiplex Sherlock assay to detect major lineages of P. pluvialis.Validation of the SHERLOCK assay quantitation of sporulation.
Project Methods
Aim 1. Characterize the variation in susceptibility to P. pluvialis within and among populations of Douglas-fir and western hemlock. a. Genotype western hemlock and Douglas-fir populations from the US and UK. The range of both western hemlock and Douglas-fir in the western US is subdivided into provenances. These provenances were created to ensure that trees grown for forest regeneration purposes were adapted to the local climate. P. pluvialis is found within the coastal forests of Oregon, southern Washington, and northern California. This distribution spans approximately 17 seed zones. From each of the 17 seed zones, 100 randomly selected seeds for both Douglas-fir and western hemlock will be provided. The 1700 seeds/species will be germinated and grown under greenhouse conditions. Following germination and growth, seedlings will have needle tissue sampled, DNA extracted, and be genotyped using the Axiom array. To compare host population genetic diversity in the US to the UK, collaborators will provide lyophilized needle tissue from western hemlock and Douglas-fir trees collected in the two regions, where the P. pluvialis outbreak occurred. Needles will be collected from 100 individuals/species/region. Once seedlings have reached a sufficient size, ~100 mg of needle tissue will be collected, frozen, and lyophilized for DNA extraction with a QiagenPlant DNA mini kit. SNP data obtained from the Axiom array will be surveyed to determine population genetic structure and diversity within the two tree species. We will use ADMIXTURE and PCA plots to analyze SNP data to compare population genetic structure and gene flow between populations within the two tree taxa.b. Evaluate differences in susceptibility among populations of Douglas-fir and western hemlock. A total of 2,470 Douglas-fir (n = 1,235) and western hemlock (n = 1,235) will have been genotyped above (Table 1). We will use the seedlings from the US provenances for the inoculation experiments (Douglas-fir = 1,105 and western hemlock = 1,105). Isolates for the inoculation experiments will be selected from our re-sequenced population representing major clades within P. pluvialis pandemic population [US (n = 9), UK (n = 2) and NZ (n = 2)]. One isolate from each clade will be selected to inoculate 10 trees from each provenance (13 P. pluvialis clades X 17 Provenances X 10 reps X = 2,210 individuals). The experimental design will be a randomized complete block design.Sporangia produced from 13 isolates will be used to inoculate 2-year-old Douglas-fir and western hemlock seedlings. Approximately 20 ml of inoculum, with a concentration of 200 to 300 sporangia/ml, will be applied to each seedling using an airbrush sprayer. Racks of inoculated trees will be enclosed in polyethylene bags for 48 h with supplemental mist. Following incubation, trees will be placed in growth chambers at 16 to 18°C with 12-h photoperiod. Phenotyping of inoculated trees will be conducted 14 days post-inoculation. Phenotypes will include: a count of the number of necrotic lesions, visual assessment of defoliation, and color spectrum of infected needles. Phenotyping data will be analyzed using mixed models.Aim 2. Evaluate the epidemiological risk to western hemlock and Douglas-fir tree farms in the USA. a. Evaluate growth and sporulation potential of representative P. pluvialis isolates across a range of temperatures in vitro and in planta.Radial growth assays. Isolates will be grown in Petri dish experiments and over a range of temperatures to determine radial growth rate and temperature optimums. Radial growth will be measured for all isolates in six replicates at 15, 20, 25°C on V8 agar medium daily.Seedling sporulation assays. Seedlings will be inoculated as described above and placed in growth chambers set to 15, 20, 25°C with 12-h photoperiod. Two weeks later infected trees will be misted with water and individually bagged to induce sporulation for counting.Needle infection efficiency. A subset of symptomatic needles (n =10) will be selected for the needle colonization assay. The 10 needles will be sampled. We will use the ratio of pathogen to host DNA as a means of quantifying host infection efficiency. Comparisons between clades and clades nested within the USA, UK, and NZ populations will be made.Statistical analysis. Analysis of variance, with linear and non-linear regression modeling, will be used to detect significant differences among treatments. Models will be developed describing dependence of disease variables (radial growth, sporulation, needle colonization) on independent variables (temperature, isolate, and isolate nested within USA, UK, or NZ populations). All statistical analyses will be conducted in R 4.2.b. Contrast infection biology of P. pluvialis on Douglas-fir and western hemlock. One susceptible provenance of Douglas-fir (n = 60 seedlings) and western hemlock (n = 60 seedlings) will be used. These plants will be inoculated, as described above, using the most virulent variant from the USA and UK. Needles and stem tissue from inoculated trees will be sampled at five different time points: 24h post-inoculation, 48h post-inoculation, 96h post inoculation, 1-week post-inoculation, and 2 weeks post inoculation. Imaging will be performed using a scanning electron microscope.We will study infection and colonization of susceptible trees simultaneously.Aim 3. Develop CRISPR-Cas diagnostic assays differentiating variants belonging to select clades. a. Validation of the SHERLOCK assay quantification of sporulation in the lab and the field. SHERLOCK. All assays will be validated using extracted DNA as well as plant samples infected with the pathogen genotype or variant of interest in live plant leaves or stems. Because validation is done in a diagnostic setting, there is opportunity for us to compare findings from conventional approaches versus those from the CRISPR-dx methods. Infections will be done under containment following USDA APHIS protocols where required. All assays will include positive controls (target lineage/species/plasmid of interest) as well as negative controls (non-target species/lineages/plasmids, etc.; water-only controls).Specificity. Specificity for all assays will be determined in triplicate using extracted DNA, sporangial (Phytophthora) suspensions, and infected plant material or pure culture DNA. Specificity will be determined with a panel of non-target relatives including a selection of Phytophthora species (P. nemorosa, P. pseudosyringae, P. psychrophila and P. ilicis). Negative controls will include non-target oomycete, fungal, and bacterial species.Sensitivity. Sensitivity will be defined as the limit of detection (LOD) that successfully detects 95% or greater of samples at the lowest concentration of the target organism. We will serially dilute either a known number of sporangia/cells (starting with 10,000 sporangia/cells per ul over a log range from 0.1-10,000 sporangia/cells per µl) or a known DNA concentration. A regression analysis of Ct values versus the log of DNA concentration will be conducted. Water will be included as a negative control. LOD will be evaluated for each concentration with 6 replications in three independent runs performed on different days.Field validation. Select field samples from Oregon forests will be used to validate the assay. A total of 30 symptomatic needles will be collected from field sites with symptomatic trees. We will use qPCR, SHERLOCK, and conventional plating on selective media to compare the specificity and sensitivity of SHERLOCK to traditional diagnostic tools.Data analysis. Student t-tests will be used to determine significance of differences (P < 0.05) of background-subtracted fluorescence between targets and controls. LFA test line intensity will be measured based on grayscale pixel values using ImageJ software. All analyses will be done in the R computer and statistical language.

Progress 06/01/24 to 05/31/25

Outputs
Target Audience:Scientists and researchers who work on Phytophthora diseases in forest ecosystems. Natural resource managers, forest pathologists, and stakeholders responsible for managing forest land in the western United States. Foresters and landowners esponsible for managing forest land in the western United States. USFS scientists. Industrial partners and landowners. Changes/Problems: Nothing Reported What opportunities for training and professional development has the project provided?Two post docotoral scholars and one undergraduate have been trained using the funds from the project to date. The postdocs will have the opportunity to present the results from their research in year 2 and year 3 of the project at scientific meetings. This project has also given the opportunity for the post-docs to help mentor an undergraduate student interested in research. They have trained the student in both laborotory techniques and exposed the student to computation biology, statistics, and bioinformatics. How have the results been disseminated to communities of interest?The results will be disseminated in presentations at scientific meetings and filed tours with natural resource managers. What do you plan to do during the next reporting period to accomplish the goals?1.Characterize the variation in susceptibility to P. pluvialis within and among populations of Douglas-fir and western hemlock. 1. Genotype western hemlock and Douglas-fir populations from the US and the UK. The1,721 DF and 561 WH will have a needles collected, frozen, and lyophilized. DNA will be extracted using an Opentrons OT-2 lab robot with a QiagenPlant DNA mini kit. DNA from each sample will then be adjusted to a minimum concentration of 20 ng/uL. DNA samples will be processed using the standard Affymetrix Axiom array protocols. SNP data obtained from the Axiom array will be surveyed to determine population genetic structure and diversity within the two tree species. We will use ADMIXTURE and PCA plots to analyze SNP data to compare population genetic structure and gene flow between populations within the two tree taxa. ADMIXTURE models the probability of genotypes for different ancestor groups similar to the software STRUCTURE. The degree of genetic connectivity among populations will be evaluated using a minimum spanning network (MSN) constructed in the R package poppr 2.1.5 . Population differentiation will be evaluated at the different hierarchies with Nei's Gst, an Fst analog estimated in the mmod 1.13 package . Population heterozygosity will be estimated and statistically contrasted for each population, using the Hs.test function with 499 replicates using the same package. The results from this analysis wil be used to guide the selection of WH and DF for inoculation in goal 2 below. 2. Evaluate differences in susceptibility of leaves and stem tissue among populations of western hemlock and Douglas-fir. Inoculations will be conducted as follows. Briefly, sporangia produced from 13 isolates will be used to inoculate 2-year-old Douglas-fir and western hemlock seedlings. Approximately 20 ml of inoculum, with a concentration of 200 to 300 sporangia/ml, will be applied to each seedling using an airbrush sprayer. Racks of inoculated trees will be enclosed in polyethylene bags for 48 h with supplemental mist. Following incubation, trees will be placed in growth chambers at 16 to 18°C with 12-h photoperiod. Phenotyping of inoculated trees will be conducted 14 days post-inoculation. Phenotypes will include: a count of the number of necrotic lesions, visual assessment of defoliation, and color spectrum of infected needles. Phenotyping data will be analyzed using mixed models. The significance of the fixed effects of provenance, geographic origin, and clade and the random effects of block and seedling will be determined using a likelihood ratio chi-squared test. The order of testing will be determined using the default z- test. All statistical analyses will be conducted in R 4.2.1 (R Core Team 2022). Difference among isolates(clades) , and geographic origins will be compared using the emmeans package in R. Significance will be evaluated at an α = 0.05. 2. Evaluate the epidemiological risk to western hemlock and Douglas-fir tree farms in the USA. 1. Evaluate growth and sporulation potential of representative P. pluvialis isolates across a range of temperatures and on inoculated seedlings. Seedling sporulation assays. Seedlings will be inoculated as described above. Approximately 20 ml of inoculum, with a concentration of 200 to 300 sporangia/ml, will be applied, using an airbrush sprayer, to each seedling. Racks of inoculated trees will be enclosed in polyethylene bags for 48 h. Following incubation, trees will be returned to growth chambers set to 15, 20, 25°C with 12-h photoperiod. Following 14 days of incubation, infected trees will be misted with water and individually bagged to induce sporulation. Sporangia will be collected and counted. Briefly, sporulation will be determined at the end of each experiment by washing sporangia from leaves and enumerating concentration using a hemocytometer. Sporulation will be expressed as the number of sporangia produced per cm2 of leaf area. Needle infection efficiency. Following washing, a subset of symptomatic needles (n =10) will be selected for the needle colonization assay. The 10 needles will be ground in liquid nitrogen and 125 mg (wet weight) will be placed in individual tubes. A Nucleospin Plant II kit, in a 96-well plate format, will be used to extract genomic DNA from frozen needles samples. We will use the ratio of pathogen to host DNA as a means of quantifying host infection efficiency. Comparisons between clades and clades nested within the USA, UK, and NZ populations will be made as described below. Statistical analysis. Analysis of variance, with linear and non-linear regression modeling, will be used to detect significant differences among treatments. Models will be developed describing dependence of disease variables (radial growth, sporulation, needle colonization) on independent variables (temperature, isolate, and isolate nested within USA, UK, or NZ populations). All statistical analyses will be conducted in R 4.2.1 (R Core Team 2022). A likelihood ratio chi-squared test will be used to evaluate the significance of variables in each model. Significance will be evaluated at an α = 0.05. 2. Contrast infection biology on Douglas-fir and western hemlock. Samples from the large scale inocualtion experiment, seedling sporulation assay, and needle infection assay will be collected. These samples will be stored and processsed in year 3 fo the project to compare the infection biology on WH and DF. 3. Develop and deploy a multiplex Sherlock assay to detect major lineages of P. pluvialis. 1. Validation of the SHERLOCK assay quantitation of sporulation. In the next reporting period we will ue the genomes we have assembled and annotated to selct target sites for teh SHERLOCK assay. We will test these sites to determine which we will use for the diagnostic assay and to quantify sporulation. lab and field testing will be conducted to valiadate the assay.

Impacts
What was accomplished under these goals? 1.Characterize the variation in susceptibility to P. pluvialis within and among populations of Douglas-fir and western hemlock. 1. Genotype western hemlock and Douglas-fir populations from the US and the UK. We gathered seeds of Douglas-fir (DF) and western hemlock (wh) from their native range, including Oregon (OR) and Washington (WH) in the United States, and British Columbia (BC) in Canada. We also received seeds from the United Kingdom (UK) where DF and WH were introduced from North America. In total, we collected seeds from 28 populations of DF (BC=9, WH=3, OR=12, UK=4), and 11 populations of WH (BC=3, WA=3, OR=1, UK=4). The seeds of both tree species were fully submerged in cool tap water for 24 hours, drained and surface dried at room temperature and cold stratified at 4 C? for 21 days for DF and 28 days for wh. After the cold stratification process, the seeds were spread out on a filter paper placed on top of on water- saturated kimpack (a highly absorbent 100% cellulose sterile germination paper) in a transparent tightly closed box (1 box per provenance). The boxes were then placed in growth chambers set to 30 C day, 20 C night 16/8 photo period for DF, and 20 C day, 20 C night 16/8 photo period for wh. The seedlings of both tree species were sown right upon germination in a green house maintained at 20-22 C . In total, we obtained 2,282 trees from 39 populations, 1,721 DF and 561 WH. These seedlings are currently growing in the greenhouse and and needles will be collected during the summer of 2025 for extraction and genotyping. 2. Evaluate differences in susceptibility of leaves and stem tissue among populations of western hemlock and Douglas-fir. Preliminary work has begun on this to develop a consistent and reliable assay. We will begin inoculations once the genotyping is complete and a genetically diverse panel of DF and WH host genotyopes from the US and UK can be selected for screening. 2. Evaluate the epidemiological risk to western hemlock and Douglas-fir tree farms in the USA. 1. Evaluate growth and sporulation potential of representative P. pluvialis isolates across a range of temperatures and on inoculated seedlings. We randomly selected total of 31 P. pluvialis isolates from the United States (n=10), New Zealand (n=10), United Kingdom (n=10), and Belgium (n=1). The isolates were grown on 20 ml clarified V8 media poured into 90 mm Petri dishes at 20 C? for 10-14 days. The plugs were taken from the actively growing edge of the mycelia and placed in a center of a Petri dish (V8; 20ml), on the intersection of two lines, previously drawn on each plate, in three replicates for five different temperatures, and were grown at 20 C for four days to initiate the growth. After four days, the growth was recorded by taking a photograph, and the isolates and their replicates were distributed to different temperatures (5°C, 10°C, 15°C, 20°C, 25°C). The growth of each replicate for each temperature was then recorded at days seven, ten, and fourteen. Radial growth was measured using ImageJ software and data analysis was performed in RStudio. 2. Contrast infection biology on Douglas-fir and western hemlock. This aim of the project has not yet been initiatited. Once the large scale inocualtions experiments are conducted this spring we will sample a subset of of DF and WH genotypes to conduct the comparative infection biology studies. 3. Develop and deploy a multiplex Sherlock assay to detect major lineages of P. pluvialis. 1. Validation of the SHERLOCK assay quantitation of sporulation. In order to improve the the genome assemble and annotation of P. pluvialis to facilitate the identification of variant sites for the SHERLOCK assay we conducted oxford nanopore seqeuncing of 6 representative isolates. We have used the short read sequences formt he preliminary data to polish these genome and are currently phasing and annotating the genomes. These genomes will be used to conduct assemblies of the remaining short read genome and the genetic variation captured in thepopulation will be used to selct and test sites for the CRISPR assay.

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