h tt p : / / w w w . b j m i c r o b i o l . c o m . b r /
Environmental
Microbiology
Selection,
isolation,
and
identification
of
fungi
for
bioherbicide
production
Angélica
Rossana
Castro
de
Souza
a,
Daiana
Bortoluzzi
Baldoni
b,
Jessica
Lima
a,
Vitória
Porto
a,
Camila
Marcuz
a,
Carolina
Machado
a,
Rafael
Camargo
Ferraz
d,
Raquel
C.
Kuhn
a,
Rodrigo
J.S.
Jacques
b,
Jerson
V.C.
Guedes
c,
Marcio
A.
Mazutti
a,∗ aUniversidadeFederaldeSantaMaria(UFSM),Departamentodeengenhariaquímica,SantaMaria,RS,BrazilbUniversidadeFederaldeSantaMaria(UFSM),Departamentoemciênciadosolo,SantaMaria,RS,Brazil cUniversidadeFederaldeSantaMaria(UFSM),Departamentodeprotec¸ãodeplantas,SantaMaria,RS,Brazil dUniversidadeFederaldoPampa,Sant’AnadoLivramento,RS,Brazil
a
r
t
i
c
l
e
i
n
f
o
Articlehistory:
Received19August2015
Accepted2May2016
Availableonline4October2016
AssociateEditor:FernandoDini
Andreote Keywords: Bioprospecting Diaporthe Bioproduct Liquidfermentation
a
b
s
t
r
a
c
t
Production ofa bioherbicide forbiological controlof weedsrequires a series ofsteps,
fromselectionofasuitablemicrobialstraintofinalformulation.Thus,thisstudyaimed
toselectfungiforproductionofsecondarymetaboliteswithherbicidalactivityusing
bio-logicalresourcesoftheBrazilianPampabiome.Phytopathogenicfungiwereisolatedfrom
infectedtissuesofweedsinthePampabiome.Aliquidsyntheticculturemediumwasused
forproductionofmetabolites.Thephytotoxicityoffungalmetaboliteswasassessedvia
bio-logicaltestsusingtheplantCucumissativusL.,andthemostpromisingstrainwasidentified
bymolecularanalysis.Thirty-ninefungiwereisolated,and28presentedsomephytotoxic
symptomsagainstthetargetplant.FungusVP51belongingtothegenusDiaportheshowed
themostpronouncedherbicidalactivity.TheBrazilianPampabiomeisapotentialresource
forthedevelopmentofnewandsustainablechemicalcompoundsformodernagriculture.
©2016SociedadeBrasileiradeMicrobiologia.PublishedbyElsevierEditoraLtda.Thisis
anopenaccessarticleundertheCCBY-NC-NDlicense(http://creativecommons.org/
licenses/by-nc-nd/4.0/).
Introduction
Brazilhostsapproximately20%ofthewholeworld’s
biolog-icaldiversity, whichcanbeemployedasaresourceforthe
developmentofnewandsustainableecosystemmanagement
toolsand opportunitiesforbioprospecting.1 Thislarge
bio-diversityisdistributedwithinsixbiomes.Amongthose,the
Pampabiome,whichisrestrictedtopartofRioGrandedoSul
∗ Correspondingauthor.
E-mail:mazutti@ufsm.br(M.A.Mazutti).
State,presentsdistinctcharacteristicsofvegetation,climate,
andsoiltypes,makingitauniqueecosystemontheplanet,
capableofmaintainingahighplantandanimaldiversity.
How-ever,PampaistheleastknownBrazilianbiomeintermsofits
biodiversity.2
Despiteitsimportance,Brazilianmicrobialdiversityisstill
considered largely unknown. Discovery of microorganisms
for use as a source of commercially exploitable products
maysupportprogramsfocusedontheapplicationof
biosyn-http://dx.doi.org/10.1016/j.bjm.2016.09.004
1517-8382/©2016SociedadeBrasileiradeMicrobiologia.PublishedbyElsevierEditoraLtda.ThisisanopenaccessarticleundertheCC
theticorbiodegradationprocesses.1,3Fungirepresentapart
ofthemicrofloraofnaturalecosystemsandmaybepromising
sourcesfortheproductionofvariouscompounds.Itis
esti-matedthatthereareabout150,300–263,900fungalspeciesin
Brazil.4Evidenceshowingthatbiologicalsourcescanprovide
naturalproductswithphytotoxic activity opensanew
per-spectiveforthepreservationofmicrobialspeciesinthePampa
biome.
Phytopathogenicfungiproducetoxinsthatmayplayarole
inthedevelopmentofplantdiseases.Weedsareasignificant
problemincropproduction,andtheirmanagementiscrucial
formodernagriculturetoavoidyieldlossesandtoensurefood
safety.Traditionalchemicalcontroloptionsarelimiteddueto
ecodegradation,healthhazards,andthedevelopmentof
her-bicideresistanceinweeds.5Herbicide-resistantweedsarethe
mainprobleminweedcontrolduetothenumberofweed
bio-typesresistanttoherbicidesthatconstantlyincreasesbythe
continuoususeofthe sameproductsforyears.6Inthelast
20years,nochemicalhasbeensynthesizedwithadifferent
modeofactionthanthosediscoveredsofar.7Suchcompounds
couldpresentaconsiderablepotentialasmodelsfor
develop-ingherbicideswithnewmodesofaction.8,9
Basedontheseaspects,themainobjectiveofthisworkwas
toisolatefungifromthePampabiomefortheproductionof
bioactivemoleculeswithherbicidalactivity.Thirty-nine
phy-topathogenicfungiwereisolated fromplantsofthe Pampa
biome.Theproductionofmetaboliteswasperformedinliquid
syntheticculturemedia.Thephytotoxicityofthefungiwas
assessedviabiologicaltests,andthemostpromisingstrain
wasidentifiedbymolecularanalysis.
Materials
and
methods
Isolationandselectionofmicroorganisms
Phytopathogenicfungiwereisolatedfrominfectedtissuesof
weedsofirrigatedriceandrangelandsatthreelocationsofthe
BrazilianPampabiome.Table1presentsthelocationsofthe
collectionsitesaswellastheweedscollectedateachlocation.
Thestrategyusedforcollectionwasbasedonselectingweeds
withsomesymptomsofinfection.Collectionwascarriedout
from December 2012toApril 2013indifferentareas ofthe
Pampabiome.Thesampleswerestoredpackedinplasticbags
andmaintainedat4◦CduringtransportationtotheLaboratory
ofBioprocesseswheretheisolationoffungiwascarriedout.
EachinfectedtissuewastransferredtoaPetridishcontaining
potatodextroseagar(PDA)andincubated at28◦Cforseven
daysinthedark.Afterthis,eachsamplewassubculturedthree
timestoobtainapureculture,whichwastransferredtoaPDA
slantinatesttubeandstoredat4◦C.
Liquidfermentation
Thegrowthofallphytopathogenicfungiisolatedinthe
pre-viousstepwascarriedoutinaliquidmedium,aimingatthe
productionofbioactivemoleculeswithherbicidalaction.For
thepre-inoculumproduction,myceliumfromeachtesttube
containingonefunguswasinoculatedonPDAinaPetridish
andincubatedforeightdaysat28◦C,whichwassufficientfor
thefungalgrowthtocovertheentiresurfaceoftheagar.
After-wards,theagarsurfaceinthePetridishwaswashedwith5mL
ofautoclavedwater,andthesuspensionwastransferredfor
fermentation.
Thefermentationswerecarriedoutin250-mLErlenmeyer
flasks containing125mLoffermentation mediumat28◦C,
120rpm for seven days (Innova 44R, New Brunswick). The
mediumwascomposedof(gL−1):glucose,10.0;yeastextract,
7.5;peptone,10.0;(NH4)2SO4,2.0;FeSO4·7H2O,1.0;MnSO4·H2O,
1.0;andMgSO4,0.5,andtheinitialpHwasadjustedto6.0.10
Afterthefermentation,cellswereseparatedby
centrifu-gationat4000rpmfor10min(Eppendorf,model5804R),and
thesupernatantwasfilteredthrougha0.45-mpolyvinylidene
fluoride(PVDF)membrane.Thefilteredsamplewasusedto
evaluateitsbioherbicidalactivityinthebioassay.Eachofthe
39fungiwasconsideredadifferentbioherbicide.
The activity of the bioherbicides obtained from the
phytopathogenic fungi was demonstrated using
cucum-ber (Cucumis sativus L., variety Wisconsin), a target plant
frequently used in bioassays of herbicides. A completely
Table1–Geographicalcoordinatesofcollectionpointsaswellastheinfectedweedscollectedforisolationoffungi.
Local Coordinates Infectedweed
Latitude Longitude
DonaFrancisca(DF) −29.634086 −53.353015 Commelinaerecta(Commelinaceae)
Solanumpaniculatum(Solanaceae)
Sagittariamontevidensis(Alismataceae)
Solanumerianthum(Solanaceae)
RestingaSeca(RS) −29.845675 −53.402069 Ipomoeatriloba(Convolvulaceae)
Sorghumhalepense(Poaceae)
VilaParaíso(VP) −29.325004 −54.958734 Conocliniummacrocephalum(Asteraceae)
Passifloraedulis(Passifloraceae)
Solanumstipulaceum(Solanaceae)
Solanumamericanum(Solanaceae)
Baccharisdracuntifolia(Asteraceae)
Eryngiumhorridum(Apiaceae)
randomizeddesign,composedof39treatments(eachselected
strainwas considered onetreatment) and four repetitions,
whereeachrepetitionrepresentedatraycontaining20
pro-pylene vessels with a volume of 200mL of a commercial
substrate(MacPlant®)withoutanytreatment,wasemployed.
Threeseedsweresownineachvessel, andafterthe
emer-gence, only one plant was maintained in each vessel and
transferredattheseedlingstagetoagreenhouselocatedat
theFederalUniversityofSantaMaria.Theseedsusedinthe
experimentwereobtainedfromalocalmarket anddidnot
undergoanytreatmentbeforeseeding.
Avolumeof30mLoffermentedbrothwasappliedatthe
sametimetoeachbioassayusingagardensprayer.Control
assayswereperformedusingtheculturemediuminsteadof
thefermentedbroth.After21days,plantinjurywasvisually
estimatedasapercentageofgrowthreductionincomparison
withtheuntreatedcontrols, where100%represented
com-pleteplantdeathand0%representednoeffect.11Inaddition,
other parameters were also investigated, including (i) the
heightoftheplant;(ii)thelengthoftheroot;(iii)freshweight
oftheaerialandrootparts;and(iv)dryweightoftheaerial
androotparts,whichwereevaluatedaftertheapplicationof
abioherbicide.
All treatments were normalized by dividing the value
obtainedinthetreatmentbythevalueobtainedinthecontrol
test. Basedontheplantdevelopment,the followingresults
wereobtained:“−”forinhibitionbetween0and0.95,“N”fora
zeroornon-significanteffect(0.95–1.05),and“+”foragrowth
effect(higherthan1.05).Alldataweresubjectedtotheanalysis
ofvariance(ANOVA)andtoTukey’stest(p<0.05)tocompare
themeans.
Fungalidentification
Themostpromisingfungusfortheproductionofa
bioherbi-cidewasidentified.FungalDNAwasextractedfromaliquots
Table2–Inhibitoryeffectofthefermentedbrothobtainedafterfermentationofeachisolatedfungusonthetargetplant (C.sativus).
Treatment Height(cm) Freshweight(g) Dryweight(g) Phytotoxiceffect
Aerial Root Aerial Root Aerial Root
DF11 1.23 (+) 0.98 N 1.30 (+) 1.20 (+) 0.81 (−) 1.00 N 0 DF12 0.73 (−) 0.96 N 0.69 (−) 1.63 (+) 0.78 (−) 0.78 (−) 40 DF13 0.78 (−) 0.78 (−) 0.63 (−) 1.40 (+) 0.73 (−) 0.85 (−) 30 DF21 0.60 (−) 0.94 (−) 0.65 (−) 0.93 (−) 0.69 (−) 0.83 (−) 40 DF23 0.74 (−) 1.51 (+) 0.73 (−) 1.19 (+) 0.71 (−) 0.81 (−) 10 DF24 0.73 (−) 1.08 (+) 0.59 (−) 1.52 (+) 0.70 (−) 0.65 (−) 30 DF25 1.09 (+) 0.91 (−) 1.10 (+) 1.82 (+) 1.27 (+) 1.03 N 20 DF3 1.05 N 0.98 N 0.94 (−) 1.07 (+) 0.89 (−) 0.84 (−) 10 DF41 1.05 (+) 0.91 (−) 0.96 N 1.07 (+) 1.05 N 1.23 (+) 0 DF42 1.13 (+) 1.21 (+) 1.22 (+) 1.62 (+) 1.02 N 1.35 (+) 0 RS11 0.77 (−) 0.89 (−) 0.80 (−) 1.20 (+) 0.85 (−) 0.83 (−) 10 RS12 1.01 N 0.94 (−) 0.84 (−) 1.06 (+) 0.77 (−) 1.17 (+) 0 RS13 0.71 (−) 1.02 N 0.73 (−) 1.64 (+) 0.77 (−) 0.83 (−) 30 RS22 1.24 (+) 1.01 N 1.05 (+) 1.15 (+) 1.23 (+) 1.28 (+) 0 RS24 1.21 (+) 0.95 (−) 1.19 (+) 1.33 (+) 1.12 (+) 1.05 (+) 0 RS25 0.69 (−) 1.00 N 0.83 (−) 0.88 (−) 1.04 N 1.24 (+) 30 RS26 0.64 (−) 0.90 (−) 0.68 (−) 1.43 (+) 0.66 (−) 0.78 (−) 20 VP11 1.11 (+) 0.94 (−) 1.22 (+) 1.54 (+) 1.20 (+) 1.62 (+) 0 VP14 1.19 (+) 1.10 (+) 1.15 (+) 1.62 (+) 1.12 (+) 1.32 (+) 10 VP21 1.05 N 0.95 (−) 1.12 (+) 1.40 (+) 1.02 N 1.17 (+) 0 VP22 1.19 (+) 1.10 (+) 1.26 (+) 1.24 (+) 1.20 (+) 0.99 N 0 VP23 1.08 (+) 0.94 (−) 1.39 (+) 2.45 (+) 1.23 (+) 1.03 N 0 VP41 0.96 N 0.54 (−) 1.05 N 0.98 N 0.79 (−) 0.91 (−) 20 VP43 0.88 (−) 0.50 (−) 0.91 (−) 0.99 N 0.68 (−) 0.85 (−) 20 VP44 0.98 N 0.45 (−) 1.00 N 1.13 (+) 0.76 (−) 1.04 N 10 VP45 0.84 (−) 0.57 (−) 0.92 (−) 0.98 N 0.75 (−) 0.70 (−) 40 VP51 0.65 (−) 0.82 (−) 0.89 (−) 0.80 (−) 0.64 (−) 0.78 (−) 60 VP52 0.92 (−) 0.83 (−) 0.92 (−) 0.70 (−) 0.75 (−) 0.73 (−) 20 VP53 0.74 (−) 1.50 (+) 1.05 N 1.57 (+) 1.04 N 1.04 N 20 VP55 0.77 (−) 0.79 (−) 0.74 (−) 0.74 (−) 0.75 (−) 0.89 (−) 30 VP56 1.22 (+) 0.98 N 1.11 (+) 1.28 (+) 1.12 (+) 1.68 (+) 40 VP62 0.83 (−) 1.32 (+) 1.02 N 1.51 (+) 0.95 N 2.08 (+) 10 VP63 0.89 (−) 0.58 (−) 0.94 (−) 1.29 (+) 0.85 (−) 1.19 (+) 20 VP68 0.89 (−) 1.50 (+) 1.20 (+) 1.78 (+) 1.11 (+) 1.11 (+) 20 VP72 0.91 (−) 1.26 (+) 1.06 (+) 1.62 (+) 0.81 (−) 1.44 (+) 10 VP73 0.89 (−) 1.10 (+) 0.93 (−) 1.10 (+) 0.90 (−) 0.96 N 30 VP76 1.47 (+) 0.91 (−) 1.39 (+) 1.48 (+) 1.44 (+) 1.32 (+) 0 VP81 0.94 (−) 1.21 (+) 0.98 N 1.13 (+) 0.73 (−) 0.73 (−) 10 VP88 1.07 (+) 1.12 (+) 0.90 (−) 0.60 (−) 0.83 (−) 0.83 (−) 10
ofgrowthintheliquidmediumusingtheZRFungal/Bacterial
DNAMiniPrepkit(Zymo Research).Afterextractionoftotal
DNA,theinternaltranscribedspacer1(ITS1)-5.8SrDNA-ITS2
regionofnuclearribosomalDNAwasamplifiedwithprimers
ITS1 and ITS4. The reaction of amplification was carried
outaccordingtoBaldonietal.12Amplificationofthecorrect
fragmentwas verifiedbyelectrophoresis ina1.5%agarose
gelwith1×Tris–borate–ethylenediaminetetraaceticacid(TBE)
buffer.TheDNAfragmentswerestainedwithBlueGreen
Load-ing Dye I® (LGC Biotecnologia, Cotia, Brazil) and analyzed
inultravioletlight.Theproductsofpolymerasechain
reac-tion (PCR) were purified using the GenElute PCR Clean-Up
Kit®(Sigma,St.Louis,MO,USA)followingthemanufacturer’s
instructions.Sequencingofthesampleswascarriedoutusing
theABI PRISM3100GeneticAnalyzer(Applied Biosystems).
The sequenced fragments were analyzed by the program
StadenPackage2.0.0btoobtainaconsensussequence.13The
consensussequence was deposited to GenBank (accession
number KU523580), and a comparative search of GenBank
sequenceswascarriedoutusingtheBLASTntool.The
addi-tionalsequencesretrievedfrom GenBankincludedthoseof
Brazilianspeciesdescribedforthisgenus.14Forthe
identifica-tionofthefungus,allthesequenceswerealignedusingthe
programBioEditv.7.2.5withtheClustalWalgorithm.15
Thephylogenywasreconstructedbymaximumlikelihood
basedontheanalysisoftheITSregionusingMEGA5.0.16A
total of1000bootstrap replicateswere usedforthe
recon-struction.TheKimuratwo-parameternucleotide-substitution
modelwasusedwithModelTestrunwithuniformratesand
partial deletion (95%) parameters.17 Thesequences of
Dia-portheambigua(KC343015)andDiaporthellacorylina(KC343004)
wereusedastheoutgroups.18,19
Results
and
discussion
In this work,39 phytopathogenic fungi were isolated from
weeds of the Pampa biome. Table 2 presents the results
obtainedinthebioassays.Twenty-eightfungishowed
phyto-toxiceffectsagainstthetargetplant,andthemostpronounced
effect was shown byfungusVP51 withan activity of60%.
Otherfungi(DF12,DF21,VP45,andVP56)alsoshowed
activ-ityatthelevelof40%.Thesesamefungialsoproducedgood
results in the growth inhibition ofaerial parts of the
tar-get,withareductionoftheheightandfreshweightaround
35–40%relativetothecontrol.Thegrowth inhibitionofthe
rootpartwaslesspronouncedincomparisonwiththeaerial
part.Generally,theinhibitionwasaround20%,anditdidnot
C
D
B
A
Table3–ComparisonofmeanamongtheeffectsoftreatmentsontheaerialandrootpartsofC.sativus.
Treatment Aerial Root
Height(cm) Freshweight(g) Dryweight(g) Height(cm) Freshweight(g) Dryweight(g)
DF21 0.604b 0.648b 0.688a 0.938a 0.933a 0.835a
VP51 0.650b 0.885ab 0.638a 0.824a 0.803a 0.776a
VP52 0.923a 0.922a 0.746a 0.827a 0.703a 0.733a
VP55 0.771ab 0.742ab 0.755a 0.791a 0.738a 0.889a
Differentletters(a,b)inthecolumnrepresentasignificantdifferenceat95%(p<0.05–Tukeytest).
resultintheplantdeath.Thelowherbicidalactivitymightbe relatedtothefactthattheactivemetabolitewassignificantly dilutedinthecrudeextract.However,itisimportantto con-siderthatabioherbicidemaynotnecessarilycausethesame effectonplantsasachemicalherbicide.Bioherbicideshave thepotential toprovidea competitive advantagefor grow-ingseedlingsthroughtheinfectionanddelayofthegrowth ofweedseedlings.20
Fig.1showssomeeffectsonaerialparts,suchasyellowing,
leafspots,andblight.Themostpronouncedeffectsonaerial
partswereobtainedwithfungiVP76,DF24,andVP51,which
arepresentedinFig. 1(A–C),respectively, whereitis
possi-bletocomparetheireffectswiththatofthecontrol(Fig.1D).
TheblastingsymptomseeninFig.1AandCwasalsonoticed
byChungetal.21whenevaluatingthepotentialofa
bioher-bicidefrom Plectosporiumtabacinumforgrowth inhibitionof
Sagittariatrifolia.Berneretal.22reportedthatoneofthe
phy-totoxicsymptomscausedbyfungiofthegenusCercosporella
wassmallbrownspotsonleaves.
Leafspots(Fig.1B)wereobservedinthefirst72hafterthe
applicationoftheDF24bioherbicide.Theseplantspresented
mild, irregularlydistributedlesions,havingadarkgreento
darkbrowncolor,whichwerelimitedtothesprayedleaves.
Theyellowingaroundthespotsbecamewidespreadintheleaf
blade,formingnecrosisfromthetipsandedgesofthesheet.
Theleavesthatemergedaftertheinoculationwerefreeofthe
disease.Theleafspoteffects,followedbyyellowing,werealso
describedbyYandocetal.23whoanalyzedtheeffectsofthe
fungiBipolarissacchariandDrechsleragiganteaonthecontrol
plantImperatacylindrical.
Similarsymptomswere reportedbyother authorswhen
a fermented broth was used for weed control. Inhibition
ofgrowth was alsoaphytotoxic effect ofbacterialisolates
on weeds, as observed by Weissmann et al.24 Gronwald
etal.25 obtainedareductionof31%inplantheight,
report-ing that the inhibition of growth was an important factor
in determining the action of a bioherbicide. Walker and
Tilley26alsoobservedareductioninthedryweightofSenna
Table4–Specimensincludedinthisstudy.AccessionGenbanknumbersinboldreferredtotheITSsequencesobtained fromDiaporthesp.inPampabioma,SouthernBrazil.
Species Strain Locality GenBankcode
DiaportheactinidiaeN.F.Sommer&Beraha ICMP:13683 NewZealand KC145886
Diaportheactinidiae JL2 China KT163360
DiaportheambiguaNitschke CBS187.87 Italy KC343015
DiaporthecitriF.A.Wolf CBS199.39 Italy KC343051
Diaporthecitri CBS199.39 Italy KC343051
DiaportheendophyticaR.R.Gomes,C.Glienke&Crous LGMF935 Brazil KC343070
Diaportheendophytica LGMF928 Brazil KC343068
DiaporthekongiiR.G.Shivas,S.M.Thompson&A.J.Young 042 KR024725
Diaporthekongii 021 KR024720
DiaporthemelonisBeraha&M.J.O’Brien CBS507.78 USA KC343142
Diaporthemelonis CBS435.87 Indonesia KC343141
DiaporthemiriciaeR.G.Shivas,S.M.Thompson&Y.P.Tan BRIP55662c Australia KJ197283
Diaporthemiriciae BRIP54736j Australia KJ197282
Diaporthephaseolorum(Cooke&Ellis)Sacc. M69 Brazil JQ936148
Diaporthephaseolorum 8.1.1 Ecuador KP133195
DiaportheschiniR.R.Gomes,C.Glienke&Crous CBS133181 Brazil NR111861
Diaportheschini B125 Brazil KR812222
Diaporthesp. VP51 Brazil KU523580
DiaporthetecomaeSacc.&P.Syd. CBS100547 Brazil KC343215
DiaportheterebinthifoliiR.R.Gomes,C.Glienke&Crous CBS133180 Brazil NR111862
Diaportheterebinthifolii B135 Brazil KR812223
Diaporthevexans(Sacc.&P.Syd.)Gratz CBS127.14 USA KC343229
DiaporthellacorylinaLar.N.Vassiljeva CBS121124 China KC343004
PhomopsisdiacheniiSacc. PH10-1 Lithuania KR870866
Phomopsisdiachenii PH1 CzechRepublic KR870844
PhomopsisfoeniculiDuManoir&Vegh PH03 Germany KR870843
obtusifoliatreatedwithabrothfermentedbyMyrothecium ver-rucaria.
Todetermine themost potentialtreatment forthe
pro-ductionofbioherbicides,somefungi(DF21,VP51,VP52,and
VP55)showingthehighestherbicidalactivityandthehighest
inhibitionoftheheightandweightofplantswerescreened.
Todetermine ifthere were differences amongthesefungi,
thedatafromTable2wereanalyzedbyANOVA,followedby
Tukey’s test (p<0.05). Theresults are compiled in Table3.
For the aerialpart, fungiDF21 and VP51showed the most
pronounced inhibitory effects on the plant height, which
werestatisticallydifferentfromthoseshownbytheothers.
Regardingfreshweight,theeffectshownbyfungusDF21was
statisticallydifferentfromthoseshownbytheothers,whereas
therewerenoverifiedsignificantdifferencesintheeffectson
dryweight,aswellasrootparts.Basedontheseresults,itcan
beinferredthatthefungishowedeffectsmainlyontheaerial
partsofthetarget,andthemostprominentwasVP51.This
fungusdemonstratedconsiderablephytotoxicityandaffected
morphologyofthetarget.Forthisreason,itwasselectedfor
molecularidentification.
ThemolecularanalysisoftheITS1-5.8S-ITS2regionofVP51
showeditshighsimilaritytothespeciesDiaportheschini(100%),
D.terebinthifolii(99%),andD.phaseolorum(99%)(Table4),among
thenucleotidesequencesavailableintheNationalCenterfor
BiotechnologyInformation(NCBI)database.However,no
sig-nificantdivergencesamongthesespecieswerefoundinthis
regiontoallowidentificationofVP51atthespecieslevel.The
phylogeneticcladeformeddidnotsupportthespecies
sepa-ration(lowbootstrapvalues)(Fig.2).
Therefore,thisresultisnotsufficienttoprovidefull
identi-fication, andatthis time,itisonlypossibletosay thatthe
fungusbelongs tothe genus Diaporthe.Gomes et al.14
sug-gestedredefiningtheclassificationofthespecieswithinthe
genus Diaporthebased onmorphological and cultural
char-acteristics,thematingtype,andDNAsequencestoobtaina
satisfactorydelineationofthespecieswithinthegenus
Dia-porthe.
The genus Diaporthe (anamorph: Phomopsis) belongs to
the phylum Ascomycota,subphylum Pezizomycotina, class
Sordariomycetes,orderDiaporthalescharacterizedassexual
fungi. However, some fungi in this genus present asexual
Diaporthe citri KC343051 Diaporthe citri KC343051 Diaporthe tecomae KC343215 Diaporthe vexans KC343229 Phomopsis diachenii KR870866 Phomopsis diachenii KR870844 Phomopsis foeniculi KR870843 Phomopsis foeniculi KR870842 Diaporthe melonis KC343142 Diaporthe melonis KC343141 Diaporthe kongii KR024725 Diaporthe kongii KR024720 Diaporthe phaseolorum JQ936148 Diaporthe phaseolorum KP133195 Diaporthe terebinthifolii NR111862 Diaporthe terebinthifolii KR812223 Diaporthe schini NR111861 Diaporthe schini KR812222 Isolate VP51 Diaporthe endophytica KC343070 Diaporthe endophytica KC343068 Diaporthe actinidiae KC145886 Diaporthe actinidiae KT163360 Diaporthe miriciae KJ197283 Diaporthe miriciae KJ197282 Diaporthe ambigua KC343015 Diaporthella corylina KC343004 0.02 99 98 65 79 100 91 99 99 75 96
Fig.2–PhylogeneticreconstructionoftheDiaporthesp.obtainedfromITS1-5.8S-ITS2sequences.Bootstrapvalues(in%)are frommaximumlikelihood(ML)analysis(1000bootstraps).Onlybootstrapvaluesofatleast50%areshown.
forms, leading to difficulty in identifying members of this
genusatthespecieslevel.Diaporthespp.areoftendescribed
asproducersofenzymes andsecondarymetabolites27 with
the potential as antibiotics,28 fungicides,29 and anticancer
agents,30 as well as that for preventing herbivory and
forbiologicalcontrolofweeds.31,32 Ethyl
2,4-dihydroxy-5,6-dimethylbenzoate, phomopsilactone,33 phomopxanthone A
andB,34taxol,30phomopsichalasin,35lactones,29nonenolides,
phomonol,phomotone,36andphomophenearesomeofthe
compoundsproducedbymembersofthegenus.
Someofthecompounds listed aboveshowed herbicidal
activity.PhomentrioloxinBcausedsmallnecroticspotsona
numberofplantspecies,whereasgulypyroneAcausedleaf
necrosis on Helianthus annuus plantlets.30 Cimmino et al.8
testedseveralcompoundsproducedinliquidcultureby
Pho-mopsissp.(teleomorph:Diaporthegulyae)forthecontrolofthe
annualweedCarthamuslanatus.
Conclusions
Inthiswork,39 fungiwere isolatedfromthePampabiome
withthegoalofobtainingbiomoleculeswithherbicidal
activ-ityagainstweeds.Twenty-eightfungicausedsomephytotoxic
symptoms,but themostpronouncedeffectswere obtained
withfungiDF21,VP51,VP52,andVP55.Amongthose, VP51
showedthehighestherbicidalactivityandwassubjectedto
molecularidentification.ThenucleotidesequenceofVP51was
comparedwithsequencesavailableintheNCBIdatabase,and
thefunguswasidentifiedasbelongingtothegenusDiaporthe,
membersofwhichhavealreadybeenreportedasproducers
ofbioherbicides.
Conflicts
of
interest
Theauthorsdeclarenoconflictsofinterest.
Acknowledgements
TheauthorsthankCAPES-CoordinationfortheImprovement
ofHigherEducationPersonnelandCNPQ-NationalCouncilfor
ScientificandTechnologicalDevelopmentforthescholarships
andthe StateDepartmentofDevelopment and Investment
Promotion(SDPI-RS)forthefinancialsupportofthiswork.
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