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Beech leaf disease symptoms caused by newly recognized nematode subspecies Litylenchus crenatae mccannii (Anguinata) described from Fagus grandifolia in North America

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Abstract

Symptoms of beech leaf disease (BLD), first reported in Ohio in 2012, include interveinal greening, thickening and often chlorosis in leaves, canopy thinning and mortality. Nematodes from diseased leaves of American beech (Fagus grandifolia) sent by the Ohio Department of Agriculture to the USDA, Beltsville, MD in autumn 2017 were identified as the first recorded North American population of Litylenchus crenatae (Nematology, 21, 2019, 5), originally described from Japan. This and other populations from Ohio, Pennsylvania and the neighbouring province of Ontario, Canada showed some differences in morphometric averages among females compared to the Japanese population. Ribosomal DNA marker sequences were nearly identical to the population from Japan. A sequence for the COI marker was also generated, although it was not available from the Japanese population. The nematode was not encountered in Fagus crenata (its host in Japan) living among nematode‐infested Fagus grandifolia in the Holden Arboretum, nor has L. crenatae been reported in American beech in Japan. The morphological and host range differences in North American populations are nomenclaturally distinguished as L. crenatae mccannii ssp. n. from the population in Japan. Low‐temperature scanning electron microscopy (LT‐SEM) demonstrated five lip annules and a highly flexible cuticle. Females, juveniles and eggs were imaged within buds with a Hirox Digital microscope and an LT‐SEM. Nematodes swarmed to the tips of freshly cut beech buds, but explants could not be maintained. Inoculation of fresh nematodes from infested leaves or buds to buds or leaves of F. grandifolia seedlings resulted in BLD leaf symptoms. Injuring dormant buds prior to nematode application, in fall or spring, promoted the most reliable symptom expression. The biogeography and physiology of anguinid nematode leaf galling, and potential co‐factors and transmission are discussed.
Forest Pathology. 2020;00:e12580. wileyonlinelibrary.com/journal/efp  
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https://doi.org/10.1111/efp.12580
© 2020 Blackwell Verlag GmbH
Received:30July2019 
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  Revised:24Ja nuary2020 
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  Accepted:27Januar y2020
DOI : 10.1111/efp .12580
ORIGINAL ARTICLE
Beech leaf disease symptoms caused by newly recognized
nematode subspecies Litylenchus crenatae mccannii (Anguinata)
described from Fagus grandifolia in North America
Lynn Kay Carta1| Zafar A. Handoo1| Shiguang Li1| Mihail Kantor1|
Gary Bauchan2| David McCann3| Colette K. Gabriel3| Qing Yu4| Sharon Reed5|
Jennifer Koch6| Danielle Martin7| David J. Burke8
1Mycology & Nematology Genetic Diversity
&Biolog yLaborator y,USDA-ARS,Belts ville,
MD,USA
2Soybea n Genom ics & Imp rovement
Laboratory, Electron Microscopy and
ConfocalMicroscopyUnit,USDA-ARS,
Beltsville,MD,USA
3OhioDepartmentofAgriculture,
Reynoldsburg,OH,USA
4Agriculture&A grifoodCanada,Ottawa
Research and Deve lopme nt Centre, Ott awa,
ON, Canada
5Ontario Forest Resear ch Institute, Ministr y
of Natura l Resources and Forestr y, Sault Ste.
Marie, ON, Canada
6USDA-FS,Delaware,OH,USA
7USDA-FS,Morgantown,WV,USA
8HoldenA rboretum,Kirtland,OH,USA
Correspondence
LynnK.Carta,Mycolog y&Nematology
Genetic Diversity & Biology Laboratory,
USDA-ARS,Belts ville,MD20705-2350,
USA.
Email: lynn.carta@usda.gov
Editor:StephenWoodward
Abstract
Symptoms of beech leaf disease (BLD), first reported in Ohio in 2012, include in-
terveinal greening, thickening and often chlorosis in leaves, canopy thinning and mor-
tality.NematodesfromdiseasedleavesofAmericanbeech(Fagus grandifolia) sent by
the OhioDepartment ofAgriculture tothe USDA, Beltsville, MD inautumn 2017
wereidentifiedasthefirstrecordedNorthAmericanpopulationofLitylenchus crena-
tae (Nematology, 21, 2019, 5), originally described from Japan. This and other popu-
lations from Ohio, Pennsylvania and the neighbouring province of Ontario, Canada
showed some differences in morphometric averages among females compared to
theJapanesepopulation.RibosomalDNAmarkersequenceswerenearlyidenticalto
thepopulationfromJapan. A sequenceforthe COI markerwasalsogenerated,al-
though it was not available from the Japanese population. The nematode was not en-
countered in Fagus crenata(itshostinJapan)livingamongnematode-infestedFagus
grandifoliaintheHoldenArboretum,norhasL. crenataebeenreportedinAmerican
beech inJapan. The morphological and host range differences in North American
populations are nomenclaturally distinguished as L. crenatae mccannii ssp. n. from the
populationinJapan.Low-temperaturescanningelectronmicroscopy(LT-SEM)dem-
onstrated five lip annules and a highly flexible cuticle. Females, juveniles and eggs
wereimagedwithinbudswithaHiroxDigitalmicroscopeandanLT-SEM.Nematodes
swarmed to the tips of freshly cut beech buds, but explants could not be maintained.
Inoculation of fresh nematodes from infested leaves or buds to buds or leaves of
F. grandifolia seedlings resulted in BLD leaf symptoms. Injuring dormant buds prior
to nematode application, in fall or spring, promoted the most reliable symptom ex-
pression. The biogeography and physiology of anguinid nematode leaf galling, and
potentialco-factorsandtransmissionarediscussed.
KEYWORDS
Anguinidae,digitalandscanningelectronmicroscopy,foliarnematode,hostrange,molecular
identification, morphometrics, new continent detection, new subspecies, symptom
transmission, taxonomy
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1 | INTRODUCTION
Symptoms of beach leaf disease (BLD) were first detected in north-
ern Ohio, USA in 2012 and have since been found in northern
Pennsylvania, New York, Ontario, Canada (Ewing, Hausman, Pogacnik,
Slot,&Bonello,2018)and Connecticut.SomeAmericanbeechtrees,
Fagus grandifolia Ehrh. and European beech trees, Fagus sylvatica L.
fromPerry,Ohioshowedsymptomsofdiseaseinthesummerof2017.
Specimens were sent to the Nematology Department at Ohio State
University, and the Ohio Departmentof Agriculture, Reynoldsburg,
Ohio. The beech leaf disease symptoms included interveinal darken-
ing, some puckering, crinkling and irregularly thickened leaves (Figure
1). Mature forest trees exhibited thinned crowns and branch dieback.
The interveinal darkening was similar to eriophyid mite damage, but
those bud mites were not noticed in association with infested leaves.
Nearlyangularleafspots,uponcloseinspectionwithastereo-micro-
scope, showed very small angular lesions within the darkened areas.
The appearance was similar to foliar nematode damage that appears
as larger angular lesions. BLD is associated with tree mortality within
7yearsofdetection.
Morphologically, these nematodess had a relatively large,
slender body length, short stylet length, more posterior vulva
and higher c′ value (tail length/anal body width) than most
Aphelenchoides (Shahina, 1996) and Bursaphelenchus taphrorychi
(Tomalak, Ma lewski, Gu, & Qian g, 2017) from European b eech.
Unlike Aphelenchoides or Bursaphelenchus, females also had a
small, narrow, weak median bulb and 6 lateral incisures. Upon fur-
ther inspection, it was determined to be the first population of
Litylenchus crenataeKanzakietal.(2019)fromthewesternhemi-
sphere, herein designated a new subspecies. Other populations
from Ohio, Pennsylvania and Ontario, Canada were also charac-
terizedwith molecular markers andmicroscopicanalysisof their
morphology. Nematodes stages within buds and leaves were ex-
aminedandimaged.InordertofulfilKoch'spostulates,L. crenatae
mccanniissp.n.wasusedtoinoculateotherwisehe althyAm erican
beec hs eedling si nO hio,USAandOnt ario,Ca nadagre enhouse st o
test whether BLD symptoms would result.
2 | MATERIALS AND METHODS
2.1 | Plant materials
InfestedleaveswerecollectedinSeptember,2017fromPerry,Ohio(Lake
County),USAbyan Ohio DepartmentofAgriculturenurseryinspector
fromailingAmericanbeech trees Fagus grandifolia Ehrh. and European
beech trees, Fagus sylvatica L. Other leaf specimens in 2018 were
sent from Kirtland, Ohio (Lake County), Potter County, Pennsylvania,
USA,CrawfordCounty,Pennsylvania,andElginandNorfolkCounties,
Ontario, Canada for morphological and molecular confirmation using
28Sand ITS 1,2 rDNAmarkers. Somespecimenswere dissectedfrom
leaves in water, measured and imaged using a microscope. Some leaves
weredissectedandstainedwithacidfuchsin(Byrd,Kirkpatrick,&Barker,
1983) for 5–10 days at room temperature to reveal nematodes in leaves.
2.2 | Microscopy
Nematodes from leaves were imaged on an Olympus BX51 microscope
equipped with polarization optics and with a DP73 camera (Olympus
AmericaInc.). Measurements in micrometresweretakenwith the cali-
brated measuring tool in the imaging program cellSens ver 1.6 (Olympus
America Inc.). Fixed specimens were processed for permanent slides
withthe formalin-glycerine method (Golden, 1990) andimagedwith a
Q-ImagingRetigaEXiColorDigitalCamera(Q-Imaging)attachedtoaLeica
WildMPS48LeitzDMRB compound microscope (LeicaMicrosystems).
Measurements and morphometrics were calculated on an Excel spread-
sheet.TheLT-SEMprotocolofCarta, Bauchan, Hsu,andYuceer(2010)
wasusedemployingaHitachiS-4700 fieldemissionSEM (HitachiHigh
TechnologiesAmerica,Inc.)withaQuorum CryoPrepPP2000 (Quorum
Technologies Ltd.) cryotransfer system to observe nematodes isolated
fromleavesandwithinbuds.AHiroxMXB-504RZdigitalmicroscopewas
alsousedtoobservenematodesinbuds(HiroxUSA,Inc.).
2.3 | DNA Isolation, amplification,
sequencing, alignment
2.3.1 | DNA extraction
DNAextractionwasperformedbyfreeze-thawlysiswithasinglelive
nematode in a 0.2 ml PCR tube containing 25 μl of extraction buffer
(10mMTrispH8.2,2.5mMMgCl2,50mMKCl,0.45%TWEEN20
and0.05%gelatin)(Carta&Li,2019).
FifteenspecimensfromBLDleavescollectedNovember,2017
inPerry,OhiowereprocessedforindividualDNAextraction,and
10 of them, prior to being transferred to each PCR tube, were im-
aged as vouchers for morphological and morphometrical analysis.
PCR amplification and DNA Sequencing: The 3.5 kb ribosomal
DNA(rDNA), ranging from near-full length 18S,internal transcribed
spacer(ITS),to28S(D1-D3)wasamplifiedandsequencedfromeach
of the imaged specimens using recently modified procedures of Carta
and Li (2019). Cytochrome c oxidase I (COI) was amplified by PCR with
theprimersets,COI-F1andCOI-R2(Kanzaki&Futai,2002).Allprim-
ersused for amplificationandsequencingarelistedin Table1.Each
25 µl PCR reaction was prepared with 2 µl of the extract and 23 µl of
thePCRmastermixcontaining0.625 U DreamTaq™Hot Start DNA
Polymerase(ThermoFisherScientific)perthemanufacturer'sprotocol.
ThePCRconditionsfortheCOIwere94°Cfor1min,5cyclesof94°C
for40s,45°C45s,72°C1min,35cyclesof94°Cfor40s,51°C45s,
72°C1minandfinalextensionat72°Cfor5min.PCRproductswere
visualizedwiththeLonzaFlashGel™DNAsystem(VWRInternational)
andthentreated with ExoSAP-ITreagent(Affymetrix,Inc) according
tothe manufacturer'sprotocol.DirectDNA sequencing forthe COI
    
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was performed bidirectionally with anABI BigDye Terminator v3.1
kitand in an ABI3730xlDNAAnalyzer(AppliedBiosystems) owned
bytheUSDASystematicEntomologyLab.Themarkersequencesde-
rived from Litylenchussp.specimens, 104H78and104H82werede-
positedtoGenBankwithaccessionnumbers forrDNA(MK292137,
MK292138)andCOI(MN524968,andMN524969).
SequenceswerecomparedwithClustalWinGenius(ver11.1.5)
with thos e from the type p opulation from Mo rioka, Iwate Pref., Japa n
forGenBankaccession numbers LC383723forSSU,LC383724for
D2-D3LSUandLC383725forITSrDNA.
2.4 | Nematode plant inoculations
2.4.1 | Nematode collection and quantification
Nematodes were isolated from leaves collected with severe BLD
symptoms, and a modification of the “water soaking” isolation method
(Zhen,Agudelo,&Gerard,2012)wasemployed.Inshort,5leaveswith
symptomsofBLDwerecut into 1-cm2 pieces and placed in a petri
dish containing 4% potato dextrose agar. Leaveswere than soaked
overnightinsterilewaterat22°C.Aftersoaking,theliquidcontaining
FIGURE 1 Leafsymptomsincludedarkenedgreenbands,chlorosisandnecrosis,Perry,OHFall2017(a)AmericanbeechFagus
grandifolia; (b) European beech, Fagus sylvatica images of David McCann
(a)
(b)
TABLE 1 PrimersusedforPCRandsequencing
Primers Direction Sequence (5′3′) Loci PCR Sequence Reference
18 S - C L- F3 FCT TGTCTCA AAGATTAAGCCATGCAT 18S √ √ Cart aandWick(2018)
18S-530R RGCGGCTGCTGGCACCACACTT 18S T homas (20 11)
18S-530F FAAGTCTGGTGCCAGCAGCCGC 18S Tho mas (2011)
18 S - C L- F2 FCTGTGATGCCCTTAGATGTCC 18S √ CartaandWick(2018)
18 S - C L- R7 RACCTTGTTACGACTTTTGCCCGGTTCA 18S This study
IT S - C L- F 2 FATTACGTCCCTGCCCT TTGTA 18S √ CartaandWick(2018)
rDNA1.58S RACGAGCCGAGTGATCCACCG 5.8S √ Cherry,Szalanski,ToddandPowers(1997)
AB28 RATATGCTTAAGTTCAGCGGGT 28S √ Vrain,Wakarchuk,LevesqueandHamilton(1992)
28 S - C L- F 3 FAAGAGAGAGTTAAAGAGGACGTGAA 28S This study
28 S - C L- R 1 RACTCC TTGGTCCGTGTTTCAAG 28S This study
28 S - C L- F 2 FCGACCCGTCTTGA AACAC 28S This study
28 S - C L- R RCAGCTACTAGATGGTTCGATTAGTC 28S √ √ This stud y
COI-R2 RGTAGCAGCAGTAAAATAAGC ACG COI √ √ KanzakiandFutai(2002)
COI-F1 FCCTACTATGATTGGTGGTT TTGGTAATTG COI √ √ KanzakiandFutai(2002)
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nematodes was carefully collected with a pipettor and then centri-
fugedat1 252 gfor2 mintoconcentratethenematodes.Waterwas
then removed through pipetting and nematodes resuspended into
1-mltotalvolumeofsterilewater.Approximately,200-µlofthenema-
todesuspensionwasremovedand200-µlof100%ethanolwasadded
tofixthenematodespriortoquantification.Nematodeswerecounted
using a Sedgewick rafter at a magnification of4X, on an Olympus
BH-2 dissecting microscope. Quantification wasmade to standard-
izethe numberofnematodes usedforleaf andbudinoculation.The
nematodes remaining in the sterile water were used for leaf and bud
inoculation as described below. Some nematodes treated with ethanol
werealsoretainedformorphologicalidentificationandDNAsequenc-
ing. Nematodes used for autumn tree inoculation were collected on
3 October 2018, and those used for spring bud inoculation were col-
lectedon22April2019.
2.4.2 | Tree leaf and bud inoculation
Three dif ferent types of plant inoculations were conducted; (a) new
leaf inoculation, (b) dormant bud inoculation prior to winter dormancy
and (c) dormant bud inoculation just prior to leaf out in spring. For
new leaf inoculation, mature, 1-m tall American beech trees (Fagus
grandifolia) that had been kept dormant in cold storage were placed
inawarmgreenhouse7September2018.Treesbrokedormancyand
began to grow after 2 weeks and newly emerged, fully expanded
leaves were available for inoculation in early October 2018. Four
treatments were conducted on each of four trees: uninjured leaf,
injured leaf, injured leaf that was inoculated with 100 µl of a water
suspensioncontaining400nematodes(4,000/ml),andaninjuredleaf
that was inoculated with 100 µl of a water suspension containing 80 0
nematodes (8,000/ml). Leaves were injured using a sterile dissecting
needle by making small holes in the leaf tissue and by scraping the
needle across the underside and upper side of each leaf. Leaves were
injured as this was found to produce the highest level of nematode
leafcolonizati oninprevi ouswork(Zhenetal.,2012).Afterleafi njur y,
thel eafwa sw rap ped ina11×21cmKi mwipe (Ki mbe rly-C lar k)w hich
was lightly moistened with sterile water to make it adhere to the leaf
surface. Leaves that received no nematodes had 100 µl of sterile
water added to the sur face of the leaf underneath the surrounding
Kimwipe.Theleafwasthanenclosed in asterile,plastic samplebag
to maintain moisture close to the surface of the leaf. Leaves receiving
nematodeshad 100µlofsterilewatercontainingeither400or 800
nematodesaddedtot hele afsurfacea sdes cr ibedabove.Af te rnem a-
todeap pl icati on,th el eafa ndKimwi pewereenc lo sedinaste rilesam-
ple bag to maintain leaf moisture. This was essential since nematodes
requireawaterfilmformovementtoallowtissuecolonization.Trees
were then placed in a warm greenhouse with supplemental lighting.
Bags were kept on the tre ated leaves for 3 days to allow for nematod e
colonizationandthenremoved.Treesweremaintainedinthegreen-
house with atemperature between 12–25°Cwith a12-hrday-night
cycle. Trees were monitored for 5 months until leaf senescence and
fall associated with the onset of plant dormancy.
BudinoculationsoccurredinOctober2018using4treeswith
well-developedbuds.Oneachtree,therewere4budtreatments:
uninjured bud, injured bud, uninjured bud that received a water
suspension containing 170 nematodes and 80 eggs (Table 2),
and an injured bud that received a water suspension containing
170nematodesand80eggs.Buds werewrappedwithapieceof
Kimwipe asdescribed above and wettedwithsterilewaterto in-
sure adherence to the bud surface. Then, 100 µl of sterile water
wasadded undertheKimwipe tothebud surface. The budsthat
did not receive nematodes received a sterile water control treat-
ment, but for buds receiving nematodes the sterile water suspen-
sioncontainedthenematodesasdescribedabove.Afternematode
or sterile water application, buds were carefully wrapped with
parafilm to retain moisture against the bud surface (Figure 7).
Buds were injured with a sterile dissecting needle such that 6 small
holes were poked into each injured bud to facilitate nematode
entry. Trees were then placed in a cold greenhouse where they
underwentwinterdormancy.Treeswerekeptundercold(4–10°C
withambientdaylight),dormantconditionsfor4 monthsprior to
moving plants intoaheatedgreenhouse (12–25°C)to break bud
dormancy and stimulate leaf emergence and grow th. Leaves were
then monitored for BLD as they developed.
Addit io na lbudinoculationswerealsoma deinApril2019using
two trees that had been dormant through winter. Due to low re-
covery of nematodes fromdormant budsinApril 2019,onlyone
bud on each tree could be inoculated with nematodes. Therefore
four total buds, two per tree, were treated as a part of this exper-
iment. On each tree, one bud was injured with a dissecting needle
as described above and then treated with sterile water as a no
nematode control, and a second was injured but treated with a
water suspension containing approximately 110 nematodes (see
Table 2). Buds were cover ed with a Kimwipe an d parafilm as a
part of the inoculation as described above. The trees were placed
inaheated greenhouse(12–25°C)tobreak bud dormancyunder
ambient light. Parafilm and Kimwipe were removed after3days,
and buds broke dormancy and leaves emerged 2 weeks after bud
inoculat ion. We monitore d leaves for sym ptoms of BLD as they
developed.
2.5 | DNA extraction and nematode detection post-
inoculation
DNAwasextractedfromsymptomaticleaftissuecollectedfromeach
tree and branch type. Leaftissuewascollected usinga1-cmsterile
cork corer, and 1 leaf punch of BLD symptomatic tissue was extracted
per tree.DNA wasextracted usinga bead-beatingapproach where
tissue was t ransferre d into a 1.5-ml bea d beating tube w hich con-
tained 300mgof400 µM sterileglass beads(VWR)and 200 mg of
1 mm steril e glass beads (C hemglass). Ab out 750-µl of 2% cet yltri-
methyl-am monium bromid e (CTAB) was added to ea ch tube as the
extraction buffer, and samples were bead beaten using a Precellys
homogenizer(Bertin Technologies)for 80 s to lyse cells andrelease
    
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DNA.DNAwaspurifiedfromtheextractmatrixusingphenol-chloro-
formextraction(Burke, Smemo,López-Gutiérrez,&DeForest,2012)
followed by precipitation in 20% polyethylene glycol 8,000 with
2. 5M NaC l.Pre cipit ate dDNAw assub sequentl ydrie dan ds usp end ed
in50µlTE(TrisEDTA)bufferandstoredina1.5-mllowretentionmi-
crocentrifugetube(FisherScientific)at−20°Cuntilanalysis.Weused
nematode specific ITS primers to detect nematodes within leaf and
budsamples.Forwardprimer TW81 (GT TTCCGTAGGTGAACCTGC)
andreverseprimer5.8MS(GGCGCAATGTGCATTCGA)(TanhaMaafi,
Subbotin, & Moens, 2003; Vovlas, Subbotin, Troccoli, Liebanas, &
Castillo,2008) wereusedfornematodeamplification. Amplification
reactionswereperformedinanMJResearchPTC-200thermalcycler
(Bio-RadLaboratories,Inc.).Aninitialdenaturationfor2minat94°C
wasfollowedby35cyclesofdenaturationfor30sat94°C,annealing
for45sat55°Candextensionfor3minat72°C,withafinalexten-
sionof10 min at72°C (Esmaeili, Heydari,&Ye,2017).PCR product
was visually checked using 1%agaros egels and ethidium bromide
staining. PCR product positive to nematodes was purified using a
WizardSVGelandPCRCleanUpSystem(Promega)andpurifiedPCR
usedfordirectsequencingofthenematodeITSregionusingBigDye
Terminatorchemistryanda3730DNAAnalyzer(AppliedBiosystems
Inc.). Sequences were generated through the Life Sciences Core
Laboratories Center (Cornell University). Sequences were identi-
fied with the EMBL/GenBank /DDBJ database entries and the NCBI
Blast tool through GenBank (https ://blast.ncbi.nlm.nih.gov/Blast.
cgi?PAGE_TYPE=BlastSearch).
Morphological identification of nematodes: Leaves showing BLD
symptoms and nearby bud tissue were also collected and sent to
USDA-ARSBeltsvilleformicroscopicexaminationandidentification.
Nematodes were dissected from plant tissue and stained with acid
fuchsin (Byrd et al., 1983).
3 | RESULTS
Litylenchus crenataeKanzakietal.(2019)mccanniissp.n.(Tables3‒5
andFigures2‒4).
3.1 | Description
Females have a nearly continuous,slightlyoffsetlip(Figures2a‒d,
3a,band4a,b)regionwith5annules(Figure4a,b),longandslender
body shape (Figures 2, 3a,b and 6c),the st ylet infemalesis5%of
thepharynxlengthand7%–10%ofthepharynxlengthinmales,and
there is a small, narrow, weak median bulb without an obvious valve.
Thevulval regioniskinked and irregular (Figure4c,d). Theanterior
gonadisrelativelylong[254±79(166–365)µmwheren=5],nearly
fivetimesthelengthofthepost-uterinesac.Thepost-uterinesacis
aboutthreetimesthevulvalbodywidthandonequarterofthevul-
valanaldistance( VAD).TheVADis2.8±0.3(2.3–3.3)timesthetail
length.Therectumisapproximately one quarter of thetaillength,
theanuspore-likeandobscureinmostspecimens.Thereisagradu-
ally tapering, slender, conical tail with an asymmetrically pointed,
often mucronate extension. The dist al tail in immature (Figures 2i
and4g,h)andmaturefemales(Figure4i,j)varyinshape.
3.1.1| Localities and hosts
Perry,OhioonleavesofAmericanbeechtreesFagus grandifolia Ehrh.
and European beech trees, Fagus sylvatica L. specimens collected
inSeptember 2017 and received between 9/12/17,and 05/18/18;
Fagus grandifoliaspecimensfromHoldenArboretum,Kirtland, OH
TABLE 2 Litylenchus crenatae mccannii ssp. n. Leaf and bud inoculation results based on results obtained through 6 May 2019
Sample ID Date Treat Control Injury + Control
Injury + 400
Nematodes Injury + 800 Nematodes Notes
Leaf Tree 1 10- 3 -18 Negative Negative Negative Negative See below
Leaf Tree 2 10- 3 -18 Negative Negative Negative Negative
Leaf Tree 3 10- 3 -18 Negative Negative Negative Negative
LeafTree4 10 - 3 -18 Negative Negative Negative Negative
Sample ID Date Treat Control Injur y + Control
170 Nematodes + 80
eggs
Injury + 170
Nematodes + 80 eggs
Bud Tree 1 10 - 3-18 Negative Negative Negative Not open (dead?)
Bud Tree 2 10 - 3-18 Negative Negative Negative Positive BLD
Bud Tree 3 10 - 3-18 Negative Negative Positive BLD Positive (slight)
BudTree4 10 - 3 -18 Negative Negative Negative Positive (slight)
Bud Tree 5 4-23 -19 NA Negative NA Positive BLD May 6 open
Bud Tree 6 4-23 -19 NA Negative NA Positive BLD May 6 open
Note: ForBudtreeinoculation1–4,redandyellowlabelreceivedabout140juvenilenematodes,30adultnematodesand80eggsperbudif
inoculated.
Forbudtrees5–6theyreceived110nematodesand40eggsonaverage.Duetolownematodeyield,weinoculatedonlyinjuredbuds.
NAequalsnotapplicable;treatmentwasnotincluded.
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TABLE 3 Morphometrics of live adult female Litylenchus crenatae mccannii ssp. n
Character
L. c. mccannii
Perry OH
9-20 17
L. c. mccannii
Kirtland, OH
10-2018
L. c. mccannii
Crawford, PA
9-20 18
L. c. mccannii
Potter, PA
10-2018
L. c. mccannii
Ontario, Canada
11-2018
n27 12 11 14 13
Body L µm 889±119(625–1084) 907.6±28.6(853.1–952.7) 739.8±178.9(562.0–1015.0) 788.8±95.2(564.4–891.2) 836±115(789–1109)
BodyWµm 14.2±1.0(12.1–16.1) 13.2±0.6(12.1–14.0) 16.2±2.4(15.0–22.0) 12.8±2.9(10.6–22.2) 14.8±2.2(13.6–15.9)
Stylet µm 9.2±0.5(8.4–10.3) 9.5±0.7(8.8–11.4) 9.3±1.2(7.5–11.0) 9.6±0.8(8.8–11.5) 9.5±0.7(8.210.4)
Phary nx L µm 193.5±35.7(126.3–244.2) 209.8±6.4(200.1–221.0) 141.7±36.7(100–195) 193.7±26.9(126.0–224.1) 176.6±12.7(151.2–198.9)
PUS µm 34.3±6.1(22.7–45.0) 22.9±5.8(13.7–33.7) 27.9±11.7(17.7–64.0) 36.9±9.4(29.7–54.1)
Tail L µm 54.3±6.1(39.8–64.4) 55.6±3.1(51.6–61.9) 43.7±11.3(33.0–62.0) 50.6±6.5(31.5–57.0) 50.6±5.5(42.3–56.6)
a63.0±10.0(43.8–76.8) 68.8±4.0(64.3–78.8) 46.3±13.6(31.2–67.7) 63.5±11.8(28.6–74.7) 61.4±9.8(40.9–73.4)
b4.7±0.7(3.8–6.6) 4.3±0.2(4.1–4.6) 5.4±0.6(4.8–6.8) 4.1±0.5(3.5–5.0) 4.8±0.3(4.0–5.3)
c16.4±1.5(13.3–20.1) 16.3±0.7(15.0–17.6) 16.8±1.4(15.0–18.8) 15.7±1.7(13.4–20.2) 16.6±1.7(12.6–19.6)
c′ 5.7±0.8(4.3–7.9) 6.0±0.5(5.5–7.2) 5.3±1.2(2.2–6.8) 5.9±0.9(4.5–6.5)
V% 76.6±1.4(73–79) 77.1±0.7(76–78) 77.7±0.07(76.5–78.4) 76.6±1.0(75.3–78.3) 80.2±6.6(75.2–86.9)
PUS/VA D% 27±8(22–50) 15 20.9 25.5±3.4(20.4–30.6)
PUS/BW 2.8±0.5(1.9–3.8) 1.8±0.5(1.1–2.7) 2.3±0.7(1.6–3.9) 2.5±0.5(1.8–2.9)
    
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TABLE 4 Morphometrics of fixed and live, adult female Litylenchus crenatae mccannii ssp. n
Character
L. c. mccannii
Perry, OH,
Live, young
L. c. mccannii
Perry OH
Fixed, young
L. crenatae
Japan
Fixed, young
L. c. mccannii
N. America
Live, mature
L. crenatae
Japan,
Fixed, mature
n27 10 10 50 10
Body L µm 889±119(625–1084) 823±61(750–947) 863±33(837–915) 740–908(625–1109) 816±32(758–870)
BodyWµm 14.2±1.0(12.1–16.1) 11.4±1.1(9.9–13.5) 12.3±0.9(11.0–13.5) 12 .8 –16. 2 (1 0 .6–16 .1) 22.9±2.6(18.4–27.7)
Stylet µm 9.2±0.5(8.4–10.3) 9.7±0.9(8.5–11.2) 8±0.4(7.4–8.5) 9.3–9.6(7.5–11.4) 10.6±0.5(9.9–11.3)
Styl conus µm 4.6±0.4(3.6–5.2) 3.1±0.2(2.8–3.5) 3.3±0.2(3.9–4.6)
Phary nx L µm 193.5±35.7(126.3–244.2) 152.6±16.2(133–186) 203±5.9(192–213) 142–210 (10 0–24 4) 123±6.7(110–131)
PUS µm 34.3±6.1(22.7–45.0) 32±3.4(29–39) 23–37(14–64) 68±7.4(57–81)
Tail L µm 54.3±6.1(39.8–64.4) 48.3±6.2(34.5–56.4) 55±3.8(50–63) 44–56(31.5–64.4) 33±2.3(30–36)
a63.0±10.0(43.8–76.8) 72.9±9.3(61–86) 67.5±5.8(60.7–74.4) 46–69(31–79) 35.9±3.4(30.2–41.1)
b4.7±0.7(3.8–6.6) 5.4±0.7(4.5–6.6) 5.3±0.6(4.5–6.3) 4.1–5.4(3.3–6.8) 6.6±0.4(6.1–7.6)
c16.4±1.5(13.3–20.1) 17.4±3.3(13–25) 15.7±0.7(14.4–16.7) 15.7–16.8(12.6–20.2) 24.5±1.9(18.5–25.1)
c′ 5.7±0.8(4.3–7.9) 6.0±1.0(4.3–7.9) 6.3±0.5(5.5–7.4) 5.3–6.0(2.2–7.9) 2.9±0.3(2.5–3.3)
V% 76.6±1.4(73–79) 76.9±1.2(75–79) 77.4±0.5(76.6–78.3) 77–80(73–87) 81.5±1.0(79.4–83.2)
PUS/VA D% 27±8(22–50) 22.9±2.1(20.2–25.9) 15–25 (20–50) 57.9±7(47–73)
PUS/BW 2.8±0.5(1.9–3.8) 2.6±0.4(2.2–3.5) 1.8–2. 8 (1.1–3.9) 3.5±0.4(2.8–4)
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8/27/18; (41°62′52.2x″N, 77°93′19.5x″W) Susquehannock State
Forest,PotterCounty,PA9/6/18;(41°64′41.95″N,80°48′96.67″W)
Pymatuning Reservoir,Jamestown, Crawford County, PA 9/21/18;
ElginCounty(42°39′52.49″N,81°10′12.48″W)andNorfolkCounty,
Ontario Canada 11/2018).
3.1.2 | Specimen designation and deposition
Thirty-seven slides (T709t (holotype), T6960- 6973p (paratypes),
7108-7110p, 7113-7126p, 7182-7186p) with 260 females and 10
males and 89 juveniles from Perry, OH were deposited in the United
States DepartmentofAgricultureNematodeCollection (USDANC)
alongwith5vials(T-576-T-580p).Inaddition,5femalesand5males
fromOntario,CanadaweredepositedintheUSDANC,and20slides
(T567a-t)oftheOntariopopulationweredepositedintheCanadian
National Collection of Nematodes Ottawa.
3.2 | Diagnosis
The Litylenchus crenatae mccannii ssp. n. young female population
fixedandmountedinearlyautumnfromNor thAmericahadalonger
stylet[9.7±0.9µmn= 10(8.6–11.2)vs.8.0±0.4 (7.4–8.5)n= 10,
p< .001]µm andstyletconus[4.6(3.6–5.2) vs. 3.1 ±0.2 (2.8–3.5)
p<.001]µmthanthetypepopulationfromJapan.Thephar ynxwas
alsosignificantlyshorter(152.6±16.2vs.203±5.9µm,p < .001) in
immature females, although the “b” ratio was not dif ferent. However,
the phar ynx was longer in mature females of 3 populations (p < .001)
but not for t hose in Crawfo rd County (142 ± 36.7 vs. 123 ± 6.7)
Thepost-uterinesac in maturefemaleswas shorter (36.9 ± 9.4vs.
68±7.4,p < .001) than the Japanese population. The tail was shorter
in the fixed immature female populations (48.3 ± 6.2 vs. 55 ± 3.8
p<.01)butitwaslongerinthematurepopulations(43.7±11.3vs.
33±2.3 p < .01, and p < .001 for 3 other populations) which was
alsoreflectedindifferent c(16.8±1.4vs.24.5±1.9,p < .001) and
c′(5.3±1.2 vs.2.9±0.3,p < .001) ratios. The body width was nar-
rowerinallpopulationsofmaturefemales(16.2±2.4vs.22.9±2.6,
p < .001). The male population from Perry, Ohio also had a longer
styl et [11.2 (10.6–12) vs. 10.2 (9.9–11)] µm and st ylet conus [4.8
(4.4–5.3)vs.3.6(3.5–4.3)]µm,anda widerbody[16.7(13.5–20.3)]
µm than the fixed type population from Japan.
3.3 | Remarks
The morp hological a nd host range di fferences in N orth Ame rican
populations are nomenclaturally distinguished as L. crenatae mccan-
nii ssp. n., after the plant pathologist who first observed the nema-
todes in BLD affected leaves. Live, mature males and females (Tables
1‒3)hadagreatdeal ofvariationwithoverlappingranges,butcer-
tain differences were noted when population averages were com-
pared. The degree of dimorphism between immature and mature
TABLE 5 Morphometrics of adult male Litylenchus crenatae mccannii ssp. n
Character
L. c. mccannii
Kirtland, OH
Live 2-2018
L. c. mccannii
Crawford, PA
Live 9-2018
L. c. mccannii
Ontario, Canada
Live 5-2018
L. c. mccannii
Perry, OH
Fixed 11-2017
L. crenatae
Japan
Fixed 6-2017
n8 3 5 48
Body L µm 657±64(554–772) 586.3±73.3(502–635) 611.8±109.1(511.8–778.2) 548.0±16.7(534.5–566.7) 707±41(642–773)
BodyWµm 16.7±2.3(13.5–20.3) 15±0(15) 15.4±1.5(13.1–17.6) 15.1±2.5(12.1–16.7) 12.4±0.8(11.3–13.5)
Stylet µm 11.2±0.4(10.6–12.0) 10±0(10) 9.8±0.3(9.6–10.1) 11.1±0.5(10.5–11.4) 10.2±0.4(9.9–11.0)
Styl conus µm 4.8±0.3(4.4–5.3) 3.4±0.1(3.4–3.6) 3.6±0.3(3.5–4.3)
Phary nx L µm 143.2±11.8(124.9–159.7) 121.2±13.4(117.8–134.9) 113.9±5.0(108.5–118.1) 135±14(116–157)
Tail L µm 34.9±3.3(30.1–41.5) 33.3±3.9(29.0–36.7) 35.3±1.6(33.7–37.9) 34±2.6(30–38)
a40.0±7.8(31.1–57.3) 41.9±0.6(41.5–42.3) 45.6±2.6(41.1–47.8) 36.1±5.4(33.3–44.1) 57.2±4.7(48.9–61.9)
b4.6±0.4(4.1–5.3) 4.5±4.1(3.9–5.0) 4.8±0.2(4.6–4.9) 4.3±0.3(3.9–4.8)
c18.9±2.0(16.2–22.7) 19.1±1.9(17.0–22.7) 15.5±0. 2(15.3–15.9) 21.1±2.0(18.5–25.1)
c′ 3.2±0.2(2.9–3.5) 3.4±0.3(2.8–3.9) 3.6±0.4(3.0–4.1)
Spicule L µm 17.1±2.4(13.7–19.7) 15±0(15) 16.5±2.1(14.3–17.6) 16.3±1.4(14.9–17.6) 15.6±1.2(14.2–17.7)
Gubernaculm L µm 6.9±0.7(6.4–8.0) 6±1(5–7) 5.9±0.2(5.7–6.0) 5.3±0.8(4.3–6.1) 6.5±0.4(6.0–7.1)
    
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CARTA eT Al .
females seen in the population from Japan was less than that seen in
themultiple NorthAmericanpopulations,primarilyreflectedinthe
narrower body of mature females.
The young overwintering adults were primarily found in October
- November, and reproductive, mature females predominated in
spring through early autumn. Multiple nematode life stages, but not
males, were found within buds, and males were found within leaves
from spring through autumn. In Ontario, the young overwintering
adults were only found in leaves on the ground in the wintering
months, while mature adults could still be found in buds.
FIGURE 2 Light microscopy (LM) of Litylenchus crenatae mccanniissp.n.fixedfemalespecimens.(a–k),live,polarizedlightmicroscopy
(PLM)females(l–n);(a-b)immatureanteriorpharynx;(c,d)matureanteriorpharynx,(e)immaturemid-bodywithvulva;(f)pharyngealgland;
(g)maturevulva,post-uterinesac;(h)immaturetail.(i)maturevulva,tail;( j,k)maletailswithspicules;(l)slenderfemaletailwithmucro,
Perry,Ohio,USA;(m)obesefemaletailwithasymmetrictip,KirtlandOhio,USA;(n)maturefemalebody,egg,PotterCounty,Pennsylvania,
USA
FIGURE 3 Polarizedlightmicroscopy
(PLM) of live Litylenchus crenatae mccannii
ssp. n. (a) female; (b) male; (c) eggs; (d)
juvenile
(a) (b)
(c) (d)
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Nematodes did not sur vive on potato dex trose agar plates
with Rhizoctonia solani.Rinsed,surface-sterilizedleavesembed-
ded in either water agar or potato dextrose agar did not provide
any better yield of nematodes than strips of leaves in sterile water
from which thousands of nematodes per infested leaf could be
harvested over a few weeks. Twigs below infested buds were
cut and placed in Baermann funnels or dishes but no nematodes
emerged.
3.4 | Bud associated nematodes
Litylenchus crenatae mccannii ssp. n. adults were inoculated to freshly
dissected beech bud tips embedded in moist water agar plates that
resulted in adult females swarming onto the bud tip (Figure 6a).
Dissection demonstrated that nematodes entered the excised bud
but did not develop.
Neither bud nor leaf explant s could be maintained on water
agar. Nematode females and eggs were exposed from within buds in
March 2019 and imaged with a Hirox (Figure 5b–d) microscope and
anLT-SEM(Figure6a–c).
3.5 | Tree leaf and bud inoculation
Wefound that beechleaf inoculations failed to initiate anysymp-
tomsofBLDintrees after5months of growth(Table4).Although
some leaves developed browning or leaf margins over the course of
5 months, none developed interveinal darkening that is characteris-
ticofBLD. Wealsoobservednoleafmortality duringthe5-month
incubation until trees began to senesce and enter dormanc y. Bud
inoculation however was successful in initiating symptoms of BLD
inbuds wherenematodeswereapplied(Table4andFigure8). For
budsinoculatedinautumnpriortodormancy,atotalof3of4buds
which were injured prior to nematode inoculation showed evidence
of BLD, while the fourth bud failed to open and died. Control buds
which were injured or uninjured and which did not receive nema-
tode inoculation all opened without signs of BLD. However, injured
FIGURE 4 Low-temperaturescanningelectronmicroscopyoffemalemorphology(a)facewithstyletopening(verticalarrow),amphid
opening(lateralarrow),obliqueview;(b)lipregionofhead,lateralview;(c)vulva(toparrow)andlateralfield(lowarrow);(d)ventralviewof
vulvawithpuckeredlipsandlateralbodydepressioninlinewithvulvalopening(arrow);(e)nematodelipspressedonmid-bodyofasecond
nematode;(f)mid-bodycuticlewithsix-sectoredlipindentationsfromanothernematodeface,lateralview;conicaltailtipvariations.(g,h)
young females; (i, j) mature females
(a) (b) (c)
(d)
(e)
(f)
(g)
(h) (i) (j)
    
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CARTA eT Al .
FIGURE 5 Litylenchus crenatae
mccannii ssp. n. on and in buds. (a) LM
image of adult females swarming on bud
tip;(b–d)Hiroxmicroscopyofnematode-
infested beech bud from the Holden
Arboretum,Kirtland,Ohio,USA
(a) (b)
(c) (d)
FIGURE 6 Low-temperaturescanning
electron microscopy images of Litylenchus
crenatae mccannii ssp. n. on leaf sheath
at bud base. (a) females, juveniles, eggs
on bud sheath; (b) adult females on bud
sheath; (c) adult female on bud sheath
near leaf mesophyll
(a) (b)
(c)
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buds, even those without nematode inoculation, tended to open
more slowl y than uninjur ed leaves. Of th e 4 buds which rece ived
nematodes but were not injured, only 1 developed symptoms of BLD
while the other 3 buds opened normally and leaves appeared unaf-
fected. For spring inoculated buds, both buds which were injured
and received nematodes developed BLD symptoms even after only
2 weeks of incubation. Both buds which did not receive nematodes
opened normally and were free of BLD symptoms.
3.6 | Nematode identification and sequence identity
Leaf tissue symptomatic for BLD was extracted from trees that underwent
budinoculation.DirectsequencingofPCR productandBlastmatching
returned matches to Litylenchus crenatae with 99% identity confirm-
ing the presence of the nematode in leaves developed from inoculated
buds.GenBanksequenceaccessionnumbers:MN625146–MN625161.
LeavesfromTree4thatwerebudinoculatedwithnematodesplusnee-
dleinjurywereharvested4-22-19,afterwhichsymptomaticleaveswere
dissected and stained with acid fuchsin (Byrd et al., 1983) and stained
nematodesrecoveredafter21days(Figure9a-c).
4 | DISCUSSION
Multiplesymptomaticleavesreceivedby the USDA-ARSMNGDBL
and Agriculture Canada national nematology laboratories yielded
many nematodes of one species only. In heavily infested areas where
nematode counts were highest in symptomatic leaves, a very small
number of nematodes were occasionally found on asymptomatic
leaves, but across all samples nematodes were not found in the vast
majority of asymptomatic leaves (S. Reed unpublished data).
FIGURE 7 Inoculation of Fagus
grandifolia seedlings with nematodes.
Bud inoculation for nematodes involved
wrappingthebudwithawetKimwipe
and adding nematode suspension under
Kimwipeatbudsurface.Thebudwas
loosely wrapped in parafilm to retain
moisture and permit nematodes to
colonizeit.Photographsshowinoculation
inApril2019ofdormantbudswith
nematodes collected from field grown
trees. The “I” indicates the bud was
injured prior to inoculation
(a) (b)
FIGURE 8 Symptoms from inoculated
seedlings. (a) Bud tree two, injured with
nematodeadded.22April2019.(b)Bud
tree three, no injury with nematode
added. 29 May 2019
(a) (b)
    
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CARTA eT Al .
Litylenchus nematodes with slender and obese morphs exhibit
phenotypic plasticity as they develop, as with other nematodes in
the family Anguinidae. Sclerotized, cuticular landmark structures
like anal and vulval openings were much more difficult to identify in
youngadultsandjuveniles.However,thestronglysclerotizedfeed-
ing stylet was always distinct, and consistently larger in mature than
immature specimens.
AswithL. crenataeinJapan(Kanzakietal.,2019)andL. coprosma
in NZ (Zhao, Davies, Alexander,& Riley,2011),slender and obese
morphs coexisted during much of the year, but obese morphs pre-
dominate d in the late spring th rough autumn. A s in Japan, males
were found in leaves in late spring through autumn, but males
were not foun d within buds in No rth Americ a during Septem ber,
November, March, or June. Eggs were found in buds rather than
leaves during autumn months despite careful dissection and staining
of leaves. However, it was possible to find eggs in leaves during late
spring which hatched within leaves to produce many nematodes by
late summer.
The fine resolution COI marker generated for this population
employed the same primers designed for another phylogenetically
distantfoliarnematode(Kanzaki&Futai,2002)associatedwiththe
laboratory of the author of the description of L. crenatae, but slightly
different conditions. These included an especially thermostable
polymeraseenzymeandhigherannealingtemperatureafterthefifth
PCRcycle.Thisdifferentprotocolmayaccountforthesequencere-
ported here that was not reported for the population from Japan.
Simple leaf inoculations with nematodes from leaves failed
to produce symptoms in Ohio greenhouse tests reported here.
However, a different experiment in Sault Ste. Marie, Ontario, Canada
with two leaves per sapling injured with a needle, treated with a
largervolumenematodeinoculumbutwithasimilar540totalnem-
atodes as in Ohio, was saturated to runoff in two 2 ml doses over a
72-hrperiod. Inthis September 2018inoculationexperiment,four
out of the five surviving treated seedlings had BLD leaf symptoms at
the beginning of June 2019, while all control seedlings were free of
symptoms. Half of the initially treated seedlings were weakened by
mites in the growth chamber and succumbed to freezing tempera-
tures in a poly house. Leaves and buds of the surviving plant s may
havebeeninjuredby freezingtemperature andmites.Itispossible
that the nematodes could have entered buds in the larger inoculum
volume runoff during these ostensible leaf inoculations to produce
symptoms. Entry into buds was the most reliable route for successful
inoculation of nematodes, whether this occurred in the fall or the
spring. Nematodes could enter buds on their own, but symptoms
appeared more routinely with injur y. In nature this might be facili-
tated by some type of vectororfreezingandthawing.However,it
appearsthatfreezingduringwinterisnotnecessarytoallowsymp-
toms to develop since an early spring inoculation in the greenhouse
produced symptoms.
While foliar nematodes are fairly common, nematodes that
exist high in the tree canopy are not well-known, though endo-
phytic Aphelenchoides were recently discovered in poplar leaves
(Populus sp.) (Carta, Li, Skantar, & Newcombe, 2016). Nematodes
like Litylenchus crenatae mccannii ssp. n. within the nematode family
Anguini dae that are asso ciated with har dwood leaves havi ng sim-
ilar swollen, chlorotic-becoming-necrotic mesophyll tissue include
Litylenchus coprosma(N ew Zealand, Zha o et al., 2011), L. crenatae
(Japan,Kanzaki et al.,2019),Ditylenchus leptosoma(Korea,Geraert
& Choi, 1990) and Subanguina chilensis (Chile, Vovlas, Troccoli, &
Moreno, 20 00). Except for leaf symptoms in L. coprosma, the others
were described as galls, though they are not discrete like the seed
galls of Anguina or eriophyid mite galls. These other anguinid nem-
atode leaf gallers were implicitly assumed to be the cause of their
symptoms. Those plants were not very economically import ant nor
did those symptoms accompany serious mortality, so there was no
indication for the need to follow up with proof of nematode patho-
genicity. None of these nematodes associated with galls have been
reported to have a fundamental association with another pathogen
sincetheirdescription(Xu,Li,Ho,Alexander,&Zhao,2017;citation
updates of all species).
The sponginess of galled por tions of the BLD leaves may result
from pectinases, similar to host leaves of the related anguinid nema-
tode Ditylenchus dipsaci (Myers, 1965). Physiological investigation of
superficially similar leaf galls of the related Ditylenchus gallaeformans
(Anguinidae)andleaf-gallingmites(Eryiophidae)bothdemonstrated
increased phenolics and carotenoids that counteract oxidative and
light damage. However, the Ditylenchus nematode gall originated in
the primordium, had a vascular connection, exhibited hypertrophied
and hyperplastic mesophyll and promoted indeterminate growth.
In contrast the simpler mite gall exhibited determinate grow th in
the epidermis (Ferreira et al., 2018). Therefore, the nematode gall
affected the host plant more profoundly and systemic ally than the
gall mite. Because there is likely to be a similar vascular connec-
tion for this related anguinid leaf galler, a Litylenchus metabolite or
even an endophytic microorganism could have a profound effect
on the plant. The nematode itself might be discovered to produce
a toxin like that recently discovered in entomoparasitic nematode
Steinernema carpocapsae(Luetal.,2017).
FIGURE 9 Acidfuchsinstains(a)
female and male nematodes from peeled
beech leaf mesophyll; (b) male nematodes
stained from leaf of experimentally
inoculated seedling, May 2019. (c) female
nematode from inoculated seedling bud
May 2019
(a) (b) (c)
14 of 15 
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   CARTA eT Al.
Nematodes within the Anguinidae related to Litylenchus may
harbour toxic Rathayibacter spp. bacteria specific to their plant
hosts ( Anguina agrostis, A. funesta, A. tritici on monocots: Dorofeeva
et al., 2018 and Mesoanguina picridis on a dicot: Starodumova et al.,
2017),but this appears to bea population-specificevent among a
fewknown species (Murray et al.,2017). In any event, preliminary
evidence from subtractive leaf biome profiling by one of the authors
found no suggestion of any Rathayibacter associated with the dis-
ease. However, work is underway to better understand the nem-
atode and beech microbiomes. The microbiomes of the pinewood
nematode, and beetle vectors are expected to illuminate the patho-
genicityofpinewooddisease(Alvesetal.,2018).
Lack of symptomatic, naturally infested Fagus crenata leaves
near infested Fagus grandifolia in Nort h America sug gests F. c re n-
atamayberesistanttothepopulationfromNorth Americabutnot
fromJapan.Asaresultofthediversityofanguinidswithsimilarleaf
symptoms from the Pacific rim, that is a likely region of endemic-
ity.TheinitialNorthAmericanlocalitiesinOhio,Pennsylvania, and
NewYork,USA,andOntario,Canadaneighbour LakeErie,atrade
hub from wh ich invasive spe cies such as em erald ash bor er (EAB)
originate d (Muirhead et al., 2 006). Like EAB, h uman transpor t of
wood may have distributed this probably invasive nematode. The
nematode may have arrived on this continent through an inverte-
brate vector, as is also suspected for Bursaphelenchus antoniae that
recentlydetectedintheU.S.(Carta&Wick,2018).
Transmission.Anguinidnematodesrequirewaterfilmstomove.
Certainly, windborne rain is a likely local means of disease transmis-
sion. Inver tebrates are as well. For instance, a predatory mite was
found entangled with nematodes, and we have collec ted various
mites and insects from leaf surfaces. Spider mites were numerous
in the summer in Ohio beech stands, and they can be windborne
for many miles. There are many potential invasive beetle vectors as-
sociated w ith beech (Mor rison, Sweeney, Hugh es, & Johns, 2017;
Rabagli a, Vandenberg, & A ccivatti, 20 09) (that may be present i n
the geographic regions where BLD occurs. Finding enough of any of
these invertebrates with nematodes takes time and directed effort
howeve r.
Birds are another possible vector, as with transport of Lyme
disease through ticks (Loss, Noden, Hamer, & Hamer, 2016).
Beech nuts are a critical component of the food chain for birds in
NortheasternandAppalachian forests. Theyarehighinthe can-
opy and difficult to harvest before the birds consume them. Since
these nematodes inhabit leaf buds they may also inhabit flower
buds. If so, birds might ingest nematodes and distribute them di-
rectly. They might carry mites, ticks or insects that carry nema-
todes as well.
Whetherthenematodeitselfisthesolecauseofthedisease,ora
vector of an elusive, hidden pathogen, it has had a consistent natural
and experimental association with disease symptoms to date.
ACKNOWLEDGEMENTS
Wethank DavidChitwood, retired MNGDBL Research Leader, for
early guidance and Joseph Mowery, ECMU, USDA-ARS, Beltsville,
MDforgraphicsofscanningelectronmicrographimages.Wethank
Adam Hoke for a ssistance w ith labora tory work an d tree inocul a-
tions. Wethank Tracey OlsonandThomas Hall,PADepartmentof
Agriculture, Harrisburg, PAand Sarah Johnson, Wellsborough, PA
for samples. Mention of trade names or commercial products in this
publication is solely for the purpose of providing specific informa-
tion and does not imply recommendation or endorsement by the
U.S.DepartmentofAgriculture.USDAisanequalopportunitypro-
vider and employer.MihailKantor was supported in partbyanap-
pointment to the Research Par ticipation Program at the Mycology
andNematology Genetic Diversity and Biology LaboratoryUSDA,
ARS,Nor theastArea,Beltsville,MD,administeredbytheOakRidge
Institute for Science and Educ ation through an interagency agree-
mentbetweentheU.S.DepartmentofEnergyandUSDA-ARS.
ORCID
Lynn Kay Carta https://orcid.org/0000-0001-7793-3990
Zafar A. Handoo https://orcid.org/0000-0001-5714-5663
Mihail Kantor https://orcid.org/0000-0001-7609-104X
Colette K. Gabriel https://orcid.org/0000-0001-9089-0155
Sharon Reed https://orcid.org/0000-0002-7724-333X
David J. Burke https://orcid.org/0000-0003-1774-1617
REFERENCES
Alves, M ., Pereira, A ., Vicente , C., Matos, P., Henri ques, J., Lop es, H.,
… Henriq ues, I. (2018). The r ole of bacteria i n Pine Wilt Dise ase:
Insights from microbiome analysis. FEMS Microbiology Ecology, 94,
fiy077.https://doi.org/10.1093/femsec/fiy077
Burke, D. J., Smemo, K . A., López-Gutiérrez, J. C., & D eForest, J. L.
(2012). Soil fungi influence the distribution of microbial func tional
groups that mediate forest greenhouse gas emissions. Soil Biology
and Biochemistry, 53, 112119. https ://doi.org/10.1016/j.soilb
io.2012.05.008
Byrd,D.W.,Jr.,Kirkpatrick,T.,&Barker,K.R.(1983).Animprovedtech-
nique for clearing and staining plant tissue for detection of nema-
todes. Journal of Nematology, 14,142–143.
Cart a,L.K.,Bauchan,G.R.,Hsu,C.-Y.,&Yuceer,C.Y.(2010).Description
of Parasitorhabditis mississippii, n.sp. (Nemata: Rhabditida) from
Dendroctonus frontalisZimmermann(Coleoptera:Scolytidae).Journal
of Nematology, 42,46–54.
Cart a, L. K., & Li, S. (2019). PCR amplification of a long rDNA seg-
ment with one primer pair in agriculturally impor tant nematodes.
Journal of Nematology, 51 , e2019–e2026. https://doi.org/10.21307/
jofnem-2019-026
Cart a,L.K.,Li,S.,Skantar,A.M.,&Newcombe,G.(2016).Morphological
and Mole cular charac terization of t wo Aphelenchoides endophytic
in poplar leaves. Journal of Nematology, 48, 28–33. https ://doi.
org /10. 213 07/jofn em-2017-0 06
Cart a,L.K.,&Wick,R.L.(2018).FirstreportofBursaphelenchus antoniae
from Pinus strobus in the U.S. Journal of Nematology, 50, 473–478.
https://doi.org/10.21307/jofnem-2018-052
Cherry,T.,Szalanski,A.L.,Todd,T.C.,&Powers,T.O.(1997).Theinternal
transcribed spacer region of Belonolaimus (Nemata: Belonolaimidae).
Journal of Nematology, 29, 23–29.
Dorofee va, L. V., Starodum ova, I. P., Krauzova, V. I., Pri syazhnaya, N.
V.,Vinokurova,N. G.,Lysanskaya,V.Y.,…Evtushenko, L. I.(2018).
Rathayibacter oskolensis sp. nov., a novel actinobacterium from
Androsace Koso-poljanskii Ovcz. (Primulaceae) endemic to the
Central Russian Upland. International Journal of Systematic and
Evolutionary Microbiology, 68,1442–1447.
    
|
 15 of 15
CARTA eT Al .
Esmaeili,M.,Heydari,R.,&Ye,W.(2017).Descriptionofanewanguinid
nematode, Nothotylenchus phoenixaen. sp. (Nematoda:Anguinidae)
associated with palm date trees and it s phylogenetic relations within
thefamily Anguinidae. Journal of Nematology, 49,268–275.https://
doi.org/10.21307/jofnem-2017-072
Ewing, C. J., Hausman, C. E., Pogacnik, J., Slot, J., & Bonello, P. (2018).
Beech leaf disease: Anemerging forest epidemic.Forest Pathology,
49(2),e12488.https://doi.org/10.1111/efp.12488
Ferreira, B. G.,Oliveira, D. C.,Moreira, A. S.F.P.,Faria, A.P.,Guedes,
L. M., Fr anca, M. G . C., … Isaias , R. M. S. (2018). A ntioxidant m e-
tabolism in galls due to the extended phenotypes of the associated
organisms. PLoS ONE, 13,e0205364.https://doi.org/10.1371/journ
al.pone.0205364
Geraert, E., & Choi, Y. E. (1990). Ditylenchus leptosoma sp. n. (Nematoda:
Tylenchida), a parasite of Carpinus leaves in Korea. Nematologia
Mediterranea, 18,27–31.
Golden,A. M. (1990). Preparation and mounting nematodesfor micro-
scopicobservation.InB.M. Zuckerman,W.F.Mai,&L.R.Krusberg
(Eds.), Plant nematology laboratory manual ( pp. 197205). Amh erst,
MA:UniversityofMassachusettsAgriculturalExperimentStation.
Kanzaki,N., & Futai,K. A.(2002). PCRprimersetfor determinationof
phylogenetic relationships of Bursaphelenchus species within the xy-
lophilus group. Nematology, 4,35–41.
Kanzaki, N., Ichihara, Y., Aikawa, T., Ekino, T., & Masuya, H. (2019).
Litylenchus crenataen. sp.(Tylenchomorpha:Anguinidae) a leafgall
nematodeparasitizingFagus crenata Blume. Nematology, 21, 5–22.
Loss, S.R., Noden,B.H.,Hamer,G.L.,& Hamer,S.A. (2016).A quanti-
tative synthesisof theroleofbirds in carryingticks and tick-borne
pathogensin North America. Oecologia, 182, 947–959. https://doi.
org/10.1007/s00442-016-3731-1
Lu,D.,Macchietto,M.,Chang,D.,Barros,M.M.,Baldwin,J.,Mortazavi,
A., &Dillman,A. R. (2017).Activatedentomopathogenicnematode
infective juveniles release lethal venom proteins. PLoS Path, 13,
e1006302.https://doi.org/10.1371/journal.ppat.1006302
Morrison,A., Sweeney,J., Hughes,C., &Johns,R.C.(2017).Hitching a
ride: Fi rewood as a potenti al pathway for ran ge expansion of an ex otic
beechleaf-miningweevil,Orchestes fagi (Coleoptera: Curculionidae).
Canadian Entomologist, 149,129–137.
Muirhead, J. R.,Leung,B., Van Overdijk, C., Kelly, D. W., Nandakumar,
K., Mar chant, K. R ., & MacIsaa c, H. J. (200 6). Modelling l ocal and
long-distance dispersal of invasive emerald ash borer Agrilus pla-
nipennis (Coleopt era) in Nort h America . Diversity and Distributions,
12,71–79.https://doi.org/10.1111/j.1366-9516.2006.00218.x
Murray,T.D.,Schroeder,B.K.,Schneider,W.L.,Luster,D.G.,Sechler,
A., Roge rs, E. E., & S ubbotin, S . A. (2017). Rathayibacter toxicus,
other Rathayibacter species inducing bacterial head blight of
grasses, and the potential for livestock poisoning s. Phytopatholog y,
107,804–815.
Myers, R . F. (1965). Amylase, cellulase, invertase and pectinase in
several free-living, mycophagus, and plant-parasitic nematodes.
Nematologica, 11,441–448.
Rabaglia,R.J.,Vandenberg,N.J.,&Accivatti,R.E.(2009).Firstrecordsof
Anisandrus maiche Stark (Coleoptera: Curculionidae: Scolytinae) from
North America. Zootaxa, 2137, 23–28. https://doi.org/10.11646/
zootaxa.2137.1.2
Shahina,F.(1996).AdiagnosticcompendiumofthegenusAphelenchoides
Fischer,1894(Nematoda:Aphelenchida) withsomenewrecords of
the group from Pakistan. Pakistan Journal of Nematology, 14, 1–3 2 .
Starodumova,I.P.,Tarlachkov,S.V.,Prisyazhnaya,N.V.,Dorofeeva,L.V.,
Ariskina,E.V.,Chizhov,V.N.,…Vasilenko,O.V.(2017).Draftgenome
sequenceofRathayibactersp.str ainVKMAc-2630isolatedfromleaf
gall induced by the knapweed nematode Mesoanguina picridis on
Acroptilon repens. Genome Announcements, 5,e00650-17.
TanhaMaafi, Z., Subbotin, S.A., &Moens, M.(2003). Molecular iden-
tification ofcyst-formingnematodes(Heteroderidae)fromIran and
aphylogenybased onITS-rDNAsequences.Nematology, 5, 99–111.
h t t p s : / / d o i . o r g / 1 0 . 1 1 6 3 / 1 5 6 8 5 4 1 0 2 7 6 5 2 1 6 7 3 1
Thomas , W. K. (2011). Mole cular techniqu es. In Internatio nal Seabed
Authority (Ed.), Marine benthic nematode molecular protocol hand-
book (Nematode barcoding). Technical Study: No. 7, ISA Technical
Study Se ries (pp. 22–37). Kings ton, Jamaica: I nternational S eabed
Authorit y.
Tomalak,M.,Malewski,T.,Gu,J.F.,&Qiang,Z.F.(2017).Descriptionof
Bursaphelenchus taphrorychi sp. n. (Nematoda: Parasitaphelenchidae),
the second Bursaphelenchus species from lar val gallerie s of the
beech bark beetle, Taphrorychus bicolor (Herbst.) (Coleoptera:
Curculionidae: Scolytinae), in European beech, Fagus sylvatica L.
Nematology, 19,1217–1235.
Vovlas, N., Subbotin, S. A., Troccoli, A., Liebanas, G., & Castillo, P.
(2008). Molecular phylogeny of the genus Rotylenchus (Nematoda,
Tylenchida) and description of a new species. Zoologica Scripta, 37,
52 1–5 3 7.
Vovlas, N., Troccoli, A., & Moreno, I . (2000). Subanguina chilensis sp.
n. (Nematoda: Anguinidae), a new leaf-gall nematode parasitizing
Nothophagus obliqua, in Chile. International Journal of Nematology, 10,
1–8 .
Vrain,T.C.,Wakarchuk,D.A.,Levesque, A. C., &Hamilton,R. I.(1992).
IntraspecificrDNArestrictionfragmentlengthpolymorphismsinthe
Xiphinema americanum group. Fundamental and applied Nematology,
15,563–573.
Xu,Y.M.,Li,D.,Ho,W.,Alexander,B.J.R.,&Zhao,Z.Q.(2017).Firstre-
port of Litylenchus coprosma on Coprosma robusta. Australasian Plant
Disease Notes, 12(1),17.https://doi .org/10.10 07/s13314-017- 0242-9
Zhao,Z.Q., Davies,K .A .,Alexander,B.,&Riley,I.T.(2011).Litylenchus
coprosmagen.n.,sp.n.(Anguinata),fromleavesonCoprosma repens
(Rubiaceae)inNewZealand.Nematology, 13,29–44.
Zhen,F.,Agudelo,P.,&Gerard,P.(2012).Aprotocolforassessingresis-
tance to Aphelenchoides fragariae in Hosta cultivars. Plant Disease, 96,
1438–144 4.
How to cite this article:CartaLK,HandooZ A,LiS,etal.
Beechleafdiseasesymptomscausedbynewlyrecognized
nematode subspecies Litylenchus crenatae mccannii
(Anguinata)describedfromFagus grandifoliainNorthAmerica.
For Path. 2020;00:e12580. htt ps ://doi .org/10.1111 /efp.12 58 0
... Beech leaf disease (BLD) is a recently described foliar disease of American beech (Fagus grandifolia) in eastern North American forests that is caused by the phytophagous nematode Litylenchus crenatae ssp. mccannii (Lcm) (Burke et al. 2020, Carta et al. 2020, Ewing et al. 2019, Reed et al. 2020). This nematode is considered a subspecies of Litylenchus crenatae as described by Kanzaki et al. (2019) in association with gall-like leaf tissues of infected Japanese beech (F. ...
... Beech leaf disease (BLD) is a recently described foliar disease of American beech (Fagus grandifolia) in eastern North American forests that is caused by the phytophagous nematode Litylenchus crenatae ssp. mccannii (Lcm) (Burke et al. 2020, Carta et al. 2020, Ewing et al. 2019, Reed et al. 2020). This nematode is considered a subspecies of Litylenchus crenatae as described by Kanzaki et al. (2019) in association with gall-like leaf tissues of infected Japanese beech (F. ...
... Symptoms of BLD include interveinal banding, distortion, and thickening of leaves, as well as bud abortion (Carta et al. 2020, Ewing et al. 2019, Fearer et al. 2022. Inoculations of wounded leaves with Lcm failed to produce beech leaf disease symptoms, while inoculations of Lcm in wounded buds resulted in characteristic BLD symptoms (Carta et al. 2020). ...
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Beech leaf disease, caused by the foliar nematode Litylenchus crenatae ssp. mccannii, deforms leaves and causes defoliation in beech (Fagus spp.). We explored management of this nematode, which threatens the health of shade-tree, ornamental, and forest beech. Field and laboratory evaluations over three years demonstrated that properly timed foliar applications of fluopyram reduced counts of live nematodes by > 90%. In vitro bioassay of fluopyram yielded an EC50 of 1.2 ppm. Similarly, oxamyl was effective when applied via trunk injection or as a soil drench to trees with < 20 cm (8 in) trunk diameter early in the season, but due to a short residual, failed to protect buds from becoming colonized in the late season (i.e. fall). High mammalian and environmental toxicity of oxamyl may limit interest in its use to injection capsules. Root flare injection or soil application of abamectin, acephate, emamectin benzoate, or potassium phosphite were ineffective in suppressing nematode populations or protecting foliage. Effective treatments cannot improve the aesthetics of trees during the current season but may protect the health of the trees by limiting the numbers of nematodes that infect buds and cause damage to foliage the following season. Species used in this study: American beech, Fagus grandifolia (Ehrh.); European beech, Fagus sylvatica (L.); North American beech leaf nematode, Litylenchus crenatae ssp. mccannii (Carta et al.). Chemicals used in this study: abamectin (Aracinate and Lucid), acephate (Lepitect), emamectin benzoate (Mectinite); fluopyram (Broadform, Indemnify, and Luna Experience), horticultural oil (RES Hort Oil), oxamyl (Return), potassium phosphite (Polyphosphite 30), tebuconazole (Torque).
... (Ewing et al. 2019;Burke et al. 2020;Marra and LaMondia 2020). Since 2012, the disease has been detected in the Great Lakes Region (Ontario, CA; Ohio, Pennsylvania, New York, and Michigan, USA) and along the Atlantic Coast (Connecticut, Maine, Massachusetts, New Hampshire, New Jersey, New York, Rhode Island, and Virginia, USA) (Ewing et al. 2019;Carta et al. 2020;Marra and LaMondia 2020;Kantor et al. 2022;Vieira et al. 2022). Disease symptoms first appear as darkened interveinal tissues giving the leaf a striped appearance. ...
... The nematodes then vacate and enter the plant or tree host through wounds caused by their vectors (Mamiya and Enda 1972;Morimoto and Iwasaki 1972;Martin et al. 1973). With respect to L. crenatae mccannii, eggs and juvenile stages of the nematode have been found on the bodies of mites (Popkin 2019;Carta et al. 2020Carta et al. , 2023. Martin et al. (2023) have demonstrated a possible link between L. crenatae mccannii and avian transport as birds are known to feed on beech buds. ...
... The authors highlighted morphological and host range differences compared to the described L. crenatae nematode species from Japan (Kanzaki et al. 2019). In the current study, we were also able to distinguish between L. crenatae and L. crenatae mccannii based on a nuclear insertion and two deletions in the ITS region, as was also reported by Carta et al. (2020). Additional molecular markers such as microsatellite markers or more variable sequence makers are needed to not only differentiate between L. crenatae and L. crenatae mccannii but also to facilitate investigations into the geographic structure in nematode populations. ...
... It has previously been determined that the anguinid nematode L. crenatae subsp. mccannii is the causative agent of BLD (4,12); however, the role of other microbial taxa in BLD causation or symptomology cannot be excluded. We previously found evidence that some bacterial genera, notably Mucilaginibacter and Wolbachia, were significantly associated with leaf or bud tissue symptomatic for BLD (5). ...
... All positive PCR amplifications in this study were confirmed to be L. crenatae through direct sequencing; thus, the lack of specificity of these primers under some conditions and their use as a general nematode primer does not impact our results. Given the putative role of L. crenatae as the ultimate cause of BLD (4,12), it is not surprising that we found much higher nematode gene copy numbers in samples from sympto matic sites. Symptomatic sites typically had gene copy numbers 100-1000× higher than asymptomatic sites, which is consistent with L. crenatae being the causative agent of BLD. ...
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Beech leaf disease (BLD) is a newly emerging disease in North America that affects American beech (Fagus grandifolia). It is increasingly recognized that BLD is caused by a subspecies of the anguinid nematode Litylenchus crenatae subsp. mccannii (hereafter L. crenatae), which is likely native to East Asia. How nematode infestation of leaves affects the leaf microbiome and whether changes in the microbiome could contribute to BLD symptoms remain uncertain. In this study, we examined bacterial and fungal communities associated with the leaves of F. grandifolia across nine sites in Ohio and Pennsylvania that were either symptomatic or asymptomatic for BLD and used qPCR to measure relative nematode infestation levels. We found significantly higher levels of infestation at sites visibly symptomatic for BLD. Low levels of nematode infestation were also observed at asymptomatic sites, which suggests that nematodes can be present without visible symptoms evident. Bacterial and fungal communities were significantly affected by sampling site and symptomology, but only fungal communities were affected by nematode presence alone. We found many significant indicators of both bacteria and fungi related to symptoms of BLD, with taxa generally occurring in both asymptomatic and symptomatic leaves, suggesting that microbes are not responsible for BLD but could act as opportunistic pathogens. Of particular interest was the fungal genus Erysiphe, which is common in the Fagaceae and is reported to overwinter in buds—a strategy consistent with L. crenatae. The specific role microbes play in opportunistic infection of leaves affected by L. crenatae will require additional study. IMPORTANCE Beech leaf disease (BLD) is an emerging threat to American beech (Fagus grandifolia) and has spread quickly throughout the northeastern United States and into southern Canada. This disease leads to disfigurement of leaves and is marked by characteristic dark, interveinal banding, followed by leaf curling and drop in more advanced stages. BLD tends to especially affect understory leaves, which can lead to substantial thinning of the forest understory where F. grandifolia is a dominant tree species. Understanding the cause of BLD is necessary to employ management strategies that protect F. grandifolia and the forests where it is a foundation tree species. Current research has confirmed that the foliar nematode Litylenchus crenatae subsp. mccannii is required for BLD, but whether other organisms are involved is currently unknown. Here, we present a study that investigated leaf-associated fungi and bacteria of F. grandifolia to understand more about how microorganisms may contribute to BLD.
... This study is the first to use the Baermann funnel method in a forest setting to capture live PPNs without an extraction method. Although various hypotheses have been proposed regarding the possible means of Lcm dispersal, including windborne rain, mites, beetles, and birds [29,30], there is currently insufficient empirical data to support or refute these hypotheses. To the best of our knowledge, this is the first attempt to quantify the influence of a collective number of variables on the local spatial distribution of Lcm. ...
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Beech leaf disease (BLD), caused by the Litylenchus crenatae ssp. mccannii (Lcm) nematode, is an emerging threat to beech trees. This disease is characterized by distinct leaf symptoms, including leaf interveinal banding and thickened leaf texture, which leads to eventual tree mortality. Understanding Lcm dispersal mechanism(s) is crucial for managing BLD, yet these remain largely unknown, posing a major barrier to its effective management. This study represents a pioneering investigation into the abiotic and biotic vectors that potentially contribute to the local dispersal of Lcm in natural American beech (Fagus grandifolia) forest systems in the Northeastern United States. An experiment was set up in Stone Valley Forest, Pennsylvania (PA), using four funnel stands placed at variable distances from naturally BLD-infected beech trees. This approach enabled the recovery of active Lcm nematodes from each funnel, demonstrating their ability to naturally disperse at least 11.74 m from the nearest BLD-infected tree. The findings highlight the role of abiotic factors involved in the dispersal dynamics of Lcm, especially wind and humidity, as indicated by a generalized linear model. The current study also uncovered the incidental association of Lcm with other organisms beneath the canopy of BLD trees, including spiderwebs and caterpillars. To our knowledge, this is the first study to document the potential vectors involved in the local dispersal of Lcm, offering valuable information for the biology of this nematode, as well as insight into the development of effective BLD management strategies. The findings contribute to broader efforts in advancing the understanding of the local spread of BLD, highlighting the complex interplay of abiotic and biotic factors in this disease dispersal.
... The lack of data on costs of forest invasive pest also reflects a fundamental tradeoff 120 between proactive and reactive approaches to mitigate the impacts of forest pest invasions 121 (Williams et al. 2023): landscape-scale management of spreading invasive pests is costly to 122 intractable; but uncertainty regarding incipient and future invasions consistently precludes 123 effective prevention. For example, scientists are still learning the basic biology of L. crenatae 124 mccannii, the foliar-feeding nematode, an understudied life history in forest pathology that 125 causes Beech leaf disease and kills young and mature Fagus grandifolia, which has spread 126 rapidly in twelve years since its discovery (Ewing et al. 2019;Carta et al. 2020;Marra and 127 LaMondia 2020; Kantor et al. 2022;Vieira et al. 2023). In addition to costs and biology, 128 uncertainty of eventual ecological and social impacts persists for many pests many years after 129 their establishment. ...
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Pine Wilt Disease (PWD) has a significant impact on Eurasia pine forests. The microbiome of the nematode (the primary cause of the disease), its insect vector, and the host tree may be relevant for the disease mechanism. The aim of this study was to characterize these microbiomes, from three PWD-affected areas in Portugal, using Denaturing Gradient Gel Electrophoresis, 16S rRNA gene pyrosequencing, and a functional inference-based approach (PICRUSt). The bacterial community structure of the nematode was significantly different from the infected trees but closely related to the insect vector, supporting the hypothesis that nematode microbiome might be in part inherited from the insect. Sampling location influenced mostly the tree microbiome (P < 0.05). Genes related both with plant growth promotion and phytopathogenicity were predicted for the tree microbiome. Xenobiotic degradation functions were predicted in the nematode and insect microbiomes. Phytotoxin biosynthesis was also predicted for the nematode microbiome, supporting the theory of a direct contribution of the microbiome to tree wilting. This is the first study that simultaneously characterized the nematode, tree and insect-vector microbiomes, from the same affected areas and overall the results support the hypothesis that PWD microbiome plays an important role in the disease development.
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Bursaphelenchus taphrorychi sp. n. is described from the bark of European beech, Fagus sylvatica. All propagative stages of the nematode are numerous in larval galleries of the beech bark beetle, Taphrorychus bicolor, while dauer juveniles are transmitted to new breeding trees under the elytra of adult beetles. The new species is characterised by the body length of 782 (717-858) μm in female and 638 (475-789) μm in male, moderately slender body (a = 35.0 (31.7-36.5) and 35.5 (31.4-37.1) in female and male, respectively), spicules 12.0-16.0 μm long, lateral fields with four incisures (i.e., three bands), and the arrangement of the seven male caudal papillae (i.e., a single precloacal ventromedian papilla (P1), one pair of adcloacal ventrosublateral papillae (P2), one postcloacal pair (P3) located at ca 60% of the tail length, posterior to the cloacal aperture, and one pair (P4) of subventral papillae of a similar size as the previous pair, but with somewhat sunken tips, located near base of bursa). In the number and arrangement of caudal papillae, stout and curved spicules with prominent rostrum and condylus, small vulval flap, body narrowed posterior to vulva, four incisures in the lateral fields, and long post-uterine sac, B. taphrorychi sp. n. shares most of the key morphological characters with members of the sexdentati-group. However, the newly described species is unique amongst Bursaphelenchus species of this group by the combination of shape of female tail, shape of spicules, and some other morphometric characters. The close relation of B. taphrorychi sp. n. with members of the sexdentati-group has been confirmed by DNA sequencing and phylogenetic analysis of the 28S rDNA region. The taxonomic separation of the new species is also confirmed by the unique molecular profile of the ITS region (ITS-RFLP). In laboratory rearing, B. taphrorychi sp. n. can develop and reproduce on Botrytis cinerea cultures.