h ttp : / / w w w . b j m i c r o b i o l . c o m . b r /
Short
communication
Archaea
diversity
in
vegetation
gradients
from
the
Brazilian
Cerrado
Ademir
Sergio
Ferreira
de
Araujo
a,∗,
Lucas
Wiliam
Mendes
b,
Walderly
Melgac¸o
Bezerra
c,
Luis
Alfredo
Pinheiro
Leal
Nunes
a,
Maria
do
Carmo
Catanho
Pereira
de
Lyra
d,
Marcia
do
Vale
Barreto
Figueiredo
d,
Vania
Maria
Maciel
Melo
c aFederalUniversityofPiauí,AgriculturalScienceCenter,SoilQualityLab.,Teresina,PI,BrazilbUniversityofSaoPauloUSP,CenterforNuclearEnergyinAgricultureCENA,CellandMolecularBiologyLaboratory,Piracicaba,SP, Brazil
cFederalUniversityofCeara,LaboratóriodeEcologiaMicrobianaeBiotecnologia,Fortaleza,CE,Brazil dAgronomicInstituteofPernambuco,Recife,PE,Brazil
a
r
t
i
c
l
e
i
n
f
o
Articlehistory:
Received2March2017
Accepted25August2017
Availableonline11February2018
AssociateEditor:ValeriaOliveira
Keywords: Microbialecology Soilmicrobiology 16SrRNA Tropicalsoils
a
b
s
t
r
a
c
t
Weused16SrRNAsequencingtoassessthearchaealcommunitiesacrossa gradientof
Cerrado.Thearchaealcommunitiesdiffered acrossthegradient.Crenarcheotawasthe
mostabundantphyla,withNitrosphaeralesandNRPJasthepredominantclasses.
Eury-achaeotawasalsofoundacrosstheCerradogradient,includingtheclassesMetanocellales
andMethanomassiliicoccaceae.
©2018SociedadeBrasileiradeMicrobiologia.PublishedbyElsevierEditoraLtda.Thisis
anopenaccessarticleundertheCCBY-NC-NDlicense(http://creativecommons.org/
licenses/by-nc-nd/4.0/).
SoilmicroorganismsconstituteathirdoftheEarth’sbiomass,
playingimportantecologicalandbiogeochemicalrolesin
ter-restrialecology.Amongthemicroorganismsthatinhabitsoils,
the domainArchaea isparticularlyimportantbecause it is
abundant and plays important roles in C and N cycling.1
Thisdomain constitutes oneofthe threemajor
evolution-ary lineages of life on Earth, and although it has long
beenbelievedthattheseorganismsmainlyinhabitextreme
∗ Correspondingauthorat:SoilQualityLab.,AgriculturalScienceCenter,FederalUniversityofPiauí,Teresina,PI,Brazil.
E-mail:asfaruaj@yahoo.com.br(A.S.Araujo).
environments, previousstudiesdemonstrated thattheyare
widely distributed around the world in different types of
soils.2,3
Sincetherecognitionofthearchaealdomaininthetree
oflife,4studieshavebeenfocusedtoexploretheirpresence
and function in a wide range of environments. With the
advance ofDNA-based molecular toolsand genomic
anal-ysis, the knowledge of this domain has evolved and the
https://doi.org/10.1016/j.bjm.2017.08.010
1517-8382/©2018SociedadeBrasileiradeMicrobiologia.PublishedbyElsevierEditoraLtda.ThisisanopenaccessarticleundertheCC
Table1–VegetationdiversityindicesintheCerradoareas.19
Campograminoide Cerradostrictosensu Cerradao Florestadecidual
Plantrichnesse 4.7 11 17 18
Plantdiversityf 0.2 0.85 1.10 1.11
Plantdensityg 4.7 27.1 35.0 51.8
Vegetationh a b c d
a Andropogonfastigiatus;Aristidalongifolia;Eragrostismaypurensis.
b Andropogonfastigiatus;Aristidalongifolia;Terminaliafagifolia;Magoniapubescens;Hymenaeacourbaril;Plathymeniareticulata;Qualeagrandiflora;
Combretummellifluum;Lippiaoriganoides;Anacardiumoccidentale;Simaroubaversicolor;Vataireamacrocarpa.
c Aspidospermadiscolor;Parkiaplatycephala;Terminaliafagifolia;Piptadeniamoniliformis;Plathymeniareticulata;Qualeaparviflora;Anacardium
occiden-tale;Copaiferacoriacea;Thiloaglaucocarpa;Caseariagrandiflora.
d Aspidospermamultiflorum;Aspidospermasubincanum;Campomanesiaaromática;Casearialasiophylla;Caseariaulmifolia;Copaiferacoriacea;
Ephedran-thuspisocarpus;Piptadeniamoniliformis;Pterocarpusviolaceus;Thiloagalucocarpa.
e Species/100m2. f H/100m2. g Individual/100m2. h Speciesofplantspresent.
current archaealclassification israpidly moving. Presently,
20 archaeal phyla are recognized by small subunit RNA
databases;however,ithasbeenreportedthat14phylahave
no cultured representative.5 Most of culturable members
of Archaea belong to the two main phyla Euryarchaeota
and Crenarchaeota. Other new phyla have been proposed
inthelast years,forexample Nanoarchaeota,basedonthe
isolation of a hypertehermophilic symbiont Nanoarchaeum
equitans6andThaumarchaeota.7Mostrecently,two
superphy-lum havebeen proposed, namely(i) TACK, which includes
thephylaThaumarchaeota,Aigarchaeota,Crenarchaeotaand
Korarchaeota,8 and (ii) Asgard, which consist in a sister
group to TACK and are considered more closely related
to the original eukaryote.9 Together with the advance of
Archaea classification, their functional role in the
ecosys-temhasalsobeenthe focus ofrecentstudies.Members of
Archaeacarryoutmanystepsinthenitrogencycle,suchas
nitrate-basedrespirationanddenitrification.10Communities
ofautotrophicand heterotrophicArchaeacatalyzeironand
sulfuroxidation,whichinfluencethereleaserateofmetals
andsulfurtotheenvironment.11 Also,regardingthecarbon
cycle,allknownmethanogenorganismsbelongexclusivelyto
Archaeadomainandaregenerallyfoundinoxygen-depleted
environments.12
InBrazil,studiesregardingthediversityofArchaeahave
beenconductedforsomeimportantecosystems,suchas
Ama-zonianand Atlanticforests,13,14 aswellas inmangroves.15
InthecaseoftheBrazilianCerrado,previousstudies
investi-gatedthediversityofarchaeainsoilsfromtheCentralPlateau
andfoundthatCrenarcheotawasthemostabundantarchaeal
groupintheecosystem.3,16However,ithasbeenhypothesized
thatthevegetationandsoilconditionsintheCerradofrom
NortheasternBrazildiffersfromthoseoftheCentralPlateau.17
Therefore, the pattern of Archaea communities would be
different because the vegetation and soil conditions drive
soilmicroorganisms.Previousstudieshaveshowndifferences
betweenbacterialdiversityinthesoilsobtainedfromCerrado
intheNortheastwhencomparedtothosefromtheCentral
Plateau.18Therefore,weusednext-generationsequencingof
the 16S rRNA gene insoil samples from vegetation
gradi-entsobtainedfromCampograminoide,Cerradostrictosensu,
CerradaoandFlorestadecidualtounderstandthediversityof
ArchaeainthesoilsofCerradoinNortheasternBrazil.
The study was conductedin a preserved Brazilian
Cer-rado within SeteCidades National Park(PNSC) (04◦02-08S
and41◦40-45W),Northeast,Brazil.Thisregionpresentstwo
distinctseasons(wetanddry)withanannualaverage
temper-atureat25◦Candrainfallof1558mmdistributedinFebruary
throughApril.Weevaluatedfourdifferentareas(with1000m2
each one) inagradientofvegetation(‘Campograminoide’,
‘Cerrado stricto sensu’, ‘Cerradao’ and ‘Floresta decidual’)
(Table1;Fig.1).
Each area was separated inthree transects(replication)
wheresoilsampleswerecollectedattopsoillayer(0–20cm
depth;threepointspertransect)inMarch(wetseason),2014.
Allsoilsampleswereimmediatelystoredinsealedplasticbags
andtransportedinaniceboxtothelaboratory.Aportionofthe
soilsampleswasstoredinbagsandkeptat−20◦CforDNA
analysisandanotherportionwasair-dried,sievedthrougha
2-mmscreenandhomogenizedforchemicalanalysesusing
standardlaboratoryprotocols.20
Soil DNA was extracted from 0.5g (total humidweight)
of soil using the PowerLyzer PowerSoil DNA Isolation Kit
(MoBIO Laboratories, Carlsbad, CA, USA), according to the
manufacturer’sinstructions.ThequalityoftheextractedDNA
wascheckedwiththeNanodropND-1000spectrophotometer
(ThermoScientific,Waltham, MA,USA),and itwas
quanti-fiedbyQubit® 2.0fluorometerusingthedsDNABRAssaykit
(InvitrogenTM).TheintegrityoftheDNAwasalsoconfirmedby
electrophoresisina0.8%agarosegelwith1×TAEbuffer.The
ampliconlibraryofthearchaeal16SrRNAgeneswere
ampli-fiedusingtheregion-specificprimers(515F/806R).21Thefirst
step amplificationcomprised 25Lreaction containing the
following:14.8Lofnuclease-freewater(Certified
Nuclease-free,Promega,Madison,WI,USA),2.5Lof10×HighFidelity
PCRBuffer (Invitrogen,Carlsbad,CA, USA),1.0Lof50mM
MgSO4, 0.5L ofeach primer (10Mconcentration, 200pM
finalconcentration),1.0unitofPlatinumTaqpolymeraseHigh
Fidelity(Invitrogen,Carlsbad,CA,USA),and4.0Loftemplate
DNA(10ng).TheconditionsforPCRwereasfollows21:94◦Cfor
4mintodenaturetheDNA,with35cyclesat94◦Cfor45s,50◦C
Fig.1–MappresentingthegradientofCerradoatSeteCidadesNationalPark,Brazil.
at72◦C.Inthesecondstep,auniquepairofIlluminaNextera
XTindexes(Illumina,SanDiego,CA)wasaddedtobothends
oftheamplifiedproducts.Each50Lreactioncontainedthe
following:23.5Lofnuclease-freewater(Certified
Nuclease-free,Promega,Madison,WI,USA),5.0Lof10×HighFidelity
PCRBuffer(Invitrogen, Carlsbad,CA,USA), 4.8Lof25mM
MgSO4, 1.5LofdNTP(10mMeach),5.0LofeachNextera
XTindex(Illumina,SanDiego,CA,USA),1.0unitofPlatinum
TaqpolymeraseHighFidelity(Invitrogen,Carlsbad,CA,USA),
and5.0LofeachproductfrompreviousPCR.Theconditions
forthissecondroundPCRwereasfollows:95◦Cfor3minto
denaturetheDNA,with8cyclesat95◦Cfor30s,55◦Cfor30s,
and72◦Cfor30min,withafinalextensionof5minat72◦C.
Afterindexing,the PCRproductswerecleanedupusing
Agencourt AMPure XP – PCR purification beads (Beckman
Coulter,Brea,CA,USA),accordingtothemanufacturer’s
man-ual,andquantifiedusingthedsDNABRassayKit(Invitrogen,
Carlsbad,CA, USA) on a Qubit 2.0 fluorometer(Invitrogen,
Carlsbad,CA,USA).Oncequantified,differentvolumesofeach
librarywerepooledintoasingletubeinequimolar
concen-tration. After quantification, the molarity of the pool was
determinedanddilutedto2nM,denatured,andthendiluted
toafinalconcentrationof8.0pMwitha20%PhiX(Illumina,
SanDiego,CA,USA)spikeforloadingintotheIlluminaMiSeq
sequencingmachine(Illumina,SanDiego,CA,USA).
SequencedatawereprocessedusingQIIMEfollowingthe
UPARSEstandardpipelineaccordingtoBrazilianMicrobiome
Project22 toproduceanOTUtableand aset of
representa-tive sequences. Briefly,the reads were truncated at240bp
and quality-filteredusing amaximum expectederrorvalue
of 0.5. Pre-filtered reads were dereplicated and singletons
wereremovedandfilteredforadditionalchimerasusingthe
RDPgolddatabaseusingUSEARCH7.0.Thesesequenceswere
clusteredintoOTUsata97%similaritycutofffollowingthe
UPARSEpipeline.Afterclustering,thesequenceswerealigned
andtaxonomicallyclassifiedagainsttheGreengenesdatabase
(version13.8).23 Thesequenceswere submittedtotheNCBI
SequenceReadArchiveunderthenumberSRP091586.
Redundancy Analysis (RDA) was used to determine the
correlationbetweenarchaealcommunitystructureandsoil
physicochemicalproperties.TheOTUtablewasinitially
ana-lyzed using Detrended Correspondence Analysis (DCA) to
evaluatethegradientsizeofthespeciesdistribution,which
Table2–SoilphysicochemicalpropertiesatdifferentsitesacrossthegradientofCerrado.
Site Moisture(%) Temperature(◦C) TOC(gkg−1) pH P(mgkg−1) K(cmolckg−1) CEC(cmolckg−1)
Campograminoide 7.3c 32a 4.3c 4.5c 3.9c 1.4b 2.28b
Cerradostrictosensu 10.5b 30b 8.3b 4.3b 3.9b 1.8b 2.31b
Cerradao 11.9b 30b 9.1b 4.6b 4.5b 1.6b 2.35b
Florestadecidual 31.8a 28c 15.2a 4.9a 5.3a 3.8a 4.91a
TOC,totalorganicC;CEC,cationexchangecapacity.
Valuesfollowedbythesameletterwithineachcolumnarenotsignificantlydifferentatthe5%level,asdeterminedbyStudent’st-test.
revealingthatthebest-fitmodelforthedatawasRDA. For-ward selection (FS) and the Monte Carlo permutation test wereappliedwith 1000random permutationstoverify the significance of soil chemical properties upon a microbial community.Weusedpermutationalmultivariateanalysisof variance(PERMANOVA)24 totestwhethersamplecategories
harbored significantly different archaeal community
struc-ture.RDAplotsweregeneratedusingthesoftwareCanoco4.5
(Biometrics,Wageningen,TheNetherlands),andPERMANOVA
andalphadiversityindexwerecalculatedwiththesoftware
PAST.25Todeterminethedifferencesinabundanceofarchaeal
groupsamongsoilsamples,theStatisticalAnalysisof
Metage-nomicProfiles(STAMP)softwarepackagewasused.26TheOTU
tablewasusedasinput,andP-valueswerecalculatedusing
thetwo-sidedWelch’st-test,27whileconfidenceintervalswere
calculatedusingDPWelch’sinvertedandcorrectionwasmade
usingBenjamini–Hochbergfalsediscoveryrate.28
In this study, we examined the archaeal structure and
compositioninthesoilsfromvegetationgradientsfromthe
Cerrado.Weused16SrRNAsequencingtoassessthearchaeal
communitiesandcorrelatedthemwithsoilchemical
parame-ters.Ourresultsshowedthatsoilparametersdifferedbetween
thesamplingsites.AreasunderCampograminoide,Cerrado
strictosensuandCerradaopresentedthehighestsoil
temper-atureandthelowestN,P,K,andCECcomparedwithFloresta
decidual(Table2).Soilmoisture,pH,andTOCcontentwere
similarbetweenCerradostrictosensuandCerradao,andthey
werethelowestandhighestinCampograminoideand
Flo-restadecidual,respectively.
Thesemarkedlydifferentsoilconditions,mainlybetween
Campograminoide and Floresta decidual, exist because of
the differences in plant cover and the communities, both
ofwhichcaninfluencesoilproperties.Forexample,Campo
graminoide iscoveredmostly by grasses, whereas Floresta
decidual is covered by trees. RDA showed the differences
betweenthearchaealcommunitiesacrossthegradients(Fig.2)
andindicatedthattheFlorestadecidualwasthemostdistinct
comparedtotheotherareas.
Additionally,RDAshowedthatthecompositionofarchaea
communitieswasstronglycorrelatedwithspecificsoil
prop-ertiesacrosstheCerradogradients.Ourresultsshowedthat
thearchaealcommunityofFlorestadecidualcorrelatedwith
soilmoisture,TOC,CEC,P,K,andN.Ontheotherhand,soil
temperatureandpHcorrelatedwithCampograminoide,
Cer-radostrictosensuandCerradao.Theseresultsindicatethat
the archaeacommunity differs acrossthe gradients ofthe
Cerradoandisinfluencedbysoilconditions.BecauseCampo
graminoide,CerradostrictosensuandCerradaohadsimilar
soilconditions,theirarchaeacommunitiesweremoresimilar
1.0 -0.6 Axis 2 (9.9%) Axis 1 (16.1%) P K N CEC TOC Moisture Temperarure pH* -1.0 1.0
Fig.2–Redundancyanalysis(RDA)ofarchaealcommunity patternsandsoilcharacteristicsfromsamplesofCampo graminoide,Cerradostrictosensu,CerradaoandFloresta decidual.Arrowsindicatecorrelationbetween
environmentalparametersandarchaealprofile.The significanceofthesecorrelationswereevaluatedviathe MonteCarlopermutationtestandisindicatedby*(P<0.05).
toeachother whencomparedtoFlorestadecidual.
Accord-ingtoCatãoet al.3 thesoilconditionsdrivethedifferences
in thediversity ofArchaeain theBrazilian Cerrado. These
authorscomparedandcontrastedCerradodensoandMatade
GaleriafromtheBrazilianCerradoandfounddifferencesin
thecommunitystructuresofArchaea.Thevariedsoil
condi-tionsfoundacrossthegradientsofvegetationhaveinfluenced
the bacterial diversity.18 Interestingly,our results highlight
thesoilpHasasignificantdriverofarchaeacommunitiesin
thesesoils.AccordingtoGorres,29soilpHisthemaindriverof
archaealcommunitystructureinsoils.Thisstrongcorrelation
betweensoilpHandthemicrobialcommunitystructuremay
bebecausepHandtheotherphysicochemicalsoilparameters
aresocloselyrelated.Mostmicroorganismshave
intracellu-larpHthatvariesintherangeofpH7±1;therefore,asmall
variationoftheenvironmentalpHcouldexpose
microorgan-ismstostress.Archaeaweredetectedinallanalyzedsamples
andshowedverylowdiversitycomparedtothebacterial
com-munityfoundinthesamesamples.18Interestingly,Floresta
decidual presented the lowest alpha diversity when
com-paredtotheother areas(Fig.3).Ithasbeensuggestedthat
anenvironmentinequilibrium,suchasforest,theecosystem
functioningismaintainedbasedonlowerlevelsofdiversity,
but high abundance of microorganisms; in contrast,
envi-ronmentsunderstresswouldpresentanincreaseddiversity,
2.5 2.0 1.5 1.0 Shannon div ersity inde x 0.5 Campo graminoide Cerrado stricto sensu Cerradao Floresta decidual a a b ab
Fig.3–DiversitymeasurementbasedonShannon’sindex ofarchaealcommunitiesinsoilsfromCampograminoide, Cerradostrictosensu,CerradaoandFlorestadecidual.
themaintenanceofessentialecosystemfunctions.30
Consid-ering thatCerrado areas are more proneto environmental
stress,suchashightemperature,lowmoistureand
oligotro-phy,thehigherarchaealdiversitywouldbeexpected.
Atotalof3078reads wereclusteredin33 OTUs
accord-ingtotheGreengenestaxonomical classification.Wefound
Crenarchaeotatobethemostabundantphylaacrossthe
Cer-radogradients,amongwhichNitrosphaeralesandNRPJwere
thepredominantclasses(Fig.4).Organismsbelongingtothe
largely non-thermophilicCrenarchaeotaappeartobe
ubiq-uitousinsoilsystemsand aredominantover euryarchaeal
populationsingrasslandsoils.31
ThesefindingsagreewithpreviousstudiesintheBrazilian
Cerrado, whichhave reportedCrenarcheota asmost
domi-nantphylumandNitrosphaeralesasanimportantgroup.3,16
TherelativeabundanceofNitrosphaeralesandNRPJdiffered
across the regions. Floresta decidual showed the highest
abundanceofNitrosphaerales,whereasCampograminoide,
Cerrado stricto sensu and Cerradao showed the highest
abundanceofNRPJ.Previously,Nicolet al.32 haveindicated
thatCrenarchaeotafromsoilsmayhavespecificassociation
with plant roots, playing an important role in the
rhi-zosphere. Nitrosphaerales are importantammonia-oxidizer
organisms,33andalthoughammoniaoxidationoccursinboth
BacteriaandArchaea,thearchaealgroupdominatesinboth
soil and marine environments.34 Nitrogen-related
microor-ganisms are commonlyfound abundantlyin forestsoils,30
whichmayexplainthehigherabundanceofNitrosphaerales
inourforestsamples.Also,Navarreteetal.35showedthatthe
diversityofammonia-oxidizingarchaealcommunitiestendto
behigherinprimaryforests.Ontheotherhand,theNRPJgroup
wasmoreabundantinCerradosites.Thisgroupbelongsto
theMarineBenthicGroupA,anunculturedarchaealcluster
initiallydescribedfromcoldcontinentalslopeanddeep-sea
sediments.36 Members of this group are commonly found
in oligotrophic soils, such as boreal forests,37 which may
explainitshigherabundanceinourCerradosamples.In
sum-mary,ourresultsshowedahighabundanceofCrenarchaeota
groupsinoursamples,withdifferentialabundancebetween
sites,suggestingthatmembersofthisgroupplaydistinctand
importantrolesinthesoilecosystem.
ThephylumEuryarchaeotaisconsideredthemost
phys-iologically diverse and includes methanogens, halophiles
and thermophile organisms. Members of this phylum
were also found across the Cerrado gradients, including
the classes Metanocellales and Methanomassiliicoccaceae.
Interestingly, the Metanocellales class was detected only
at Campo graminoide, which also had a high
abun-danceofMethanomassiliicoccaceae.Similarly,Cerradostricto
sensu showed high abundance of
Methanomassiliicoc-caceae.Thefamily Methanomassiliicoccaceae comprisesof
a methanogenic lineageof theclass Thermoplasmata,and
members ofthe Methanocellales family are methanogenic
organisms,contributingtotheglobalmethanecycle.38Inthis
sense,ourresultsshowthatimportantgroupsrelatedto
car-bon cycle areabundantinCampograminoide and Cerrado
strictosensu. Euryarchaeota :Methanomassiliicoccaceae Euryarchaeota :Methanocellales Crenarchaeota : NRPJ Crenarchaeota : Nitrosphaerales b ab a a a a a a b b b b 0.01 0.1 1 10 100
Proportion of sequences (log scale)
Campo graminoide Cerrado stricto sensu Ceradao Floresta decidual
Fig.4–AveragerelativeabundanceofthemostabundantarchaealgroupsinsoilsfromCampograminoide,Cerradostricto sensu,CerradaoandFlorestadecidualasrevealedbythe16SrRNAgeneribotyping.Foreachsampletype,thenumberof replicatesisn=9.Differentlowerlettersindicatesignificantdifference(FDR,P<0.05)amongsamples.
AsshownintheRDA,pHwasthemaindriverofthearchaea
communitiesacrossthegradients.Ithasbeendescribedthat
pHdominatesthevariationofarchaealdiversityand
commu-nitycompositionintropicalsoils.39Inalarge-scalestudy,the
authorsshowedanichespecializationofterrestrialarchaeal
ammoniaoxidizersbasedonpH, showingthatamoA
abun-danceanddiversityincreasedwithsoilpH.40Inoursamples,
thehighsoilpHfoundintheFlorestadecidualareafavoredthe
dominanceofNitrosphaerales,whichissensitivetolowpH.41
Ontheotherhand,ahighabundanceofEuryachaeota,
specif-icallyMetanocellales,intheCampograminoideregionmaybe
relatedtothelowsoilpHfoundinthisarea.AccordingtoHu
etal.,41soilpHisadriverofmethanogenesisandsubsequently
maypromoteshiftsinthearchaealcommunitycomposition
fromCrenarchaeotatomethanogenicEuryarchaeota.
Inconclusion,ourdatashowedthatalthoughthemostof
detectedtaxaaresharedbetweenallfourareas,thearchaeal
structure and abundance differed across these gradients
andwasstronglydrivenbysoilphysicochemicalproperties.
The soil pH was the main driver of archaeal
communi-tiesin the studiedsoils, and this can beexplained bythe
difference between the sites, where Florestadecidual
pre-sentedhighervalueswhileCampograminoidewasmoreacid.
Resultsshowedthat Crenarcheotawas themost dominant
phylum,followedbyEuryarchaeota.Additionally,differential
soilparameters leadto distinct functional potential ofthe
communities,whereFlorestadecidualpresentedhigh
abun-dance ofgroups related to the nitrogen metabolism while
CampograminoideandCerradostrictosensupresentedhigh
abundance of groups related to carbon metabolism. Also,
Nitrosphaeraleswasthemostabundantorderfoundacross
thegradients,andfurtherstudiesareneededtoevaluatetheir
potentialinNcycling.
Conflicts
of
interest
Theauthorsdeclarenoconflictsofinterest.
Acknowledgments
Theauthorsthank“Fundac¸ãodeAmparoaPesquisanoEstado
doPiauí”(FAPEPI)forfinancialsupporttothisprojectthrough
ofPRONEX (FAPEPI/CNPq 004/2012). Wethankthe Unidade
Multiusuário doNúcleode Pesquisa eDesenvolvimento de
Medicamentos(UM-NPDM)fromFederalUniversityofCeará
forusingMiSeqIlluminasequencingfacilities.
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s
1.SchimelJ.Playingscalesinthemethanecycle:from
microbialecologytotheglobe.ProcNatlAcadSciUSA.
2004;101:12400–12401.
2.SilesJA,MargesinR.Abundanceanddiversityofbacterial,
archaeal,andfungalcommunitiesalonganaltitudinal
gradientinAlpineForestSoils:whatarethedrivingfactors?
MicrobEcol.2016;72:207–220.
3.CataoE,CastroAP,BarretoCC,KrugerRH,KyawCM.
DiversityofarchaeainBraziliansavanasoils.ArchMicrobiol.
2013;195:507–512.
4.WoeseCR,KandlerO,WheelisML.Towardsanaturalsystem
oforganisms:proposalforthedomainsArchaea,Bacteria,
andEucarya.ProcNatlAcadSciUSA.1990;87:4576–4579.
5.SchlossPD,GirardRA,MartinT.StatusoftheArchaealand
Bacterialcensus:anupdate.MBio.2016;7:e00201–e216.
6.HuberH,HohnMJ,RachelR,FuchsT,WimmerVC,Stetter
KO.AnewphylumofArchaearepresentedbyananosized
hyperthermophilicsymbiont.Nature.2002;417:63–67.
7.Brochier-ArmanetC,BoussauB,GribaldoS,ForterreP.
MesophilicCrenarchaeota:proposalforathirdarchaeal
phylum,theThaumarchaeota.NatRevMicrobiol.
2008;6:245–252.
8.GuyL,EttemaTJG.Thearchaeal‘TACK’superphylumand
theoriginofeukaryotes.TrendsMicrobiol.2011;19:
580–587.
9.Zaremba-NiedzwiedzkaK,CaceresEF,SawJH,etal.Asgard
archaeailluminatetheoriginofeukaryoticcellular
complexity.Nature.2017;541:353–358.
10.CabelloP,RoldánMD,Moreno-ViviánC.Nitratereduction
andthenitrogencycleinarchaea.Microbiology.
2004;150:3527–3546.
11.BakerBJ,BanfieldJF.Microbialcommunitiesinacidmine
drainage.FEMSMicrobiolEcol.2003;44:139–152.
12.SpangA,EttemaTJG.ThemethanogenicrootsofArchaea.
NatMicrobiol.2017;2:17109.
13.TaketaniRG,TsaiSM.infuenceofdiferentlandusesonthe
structureofarchaealcommunitiesinAmazoniananthrosols
basedon16SrRNAandamoAgenes.MicrobEcol.
2010;59:734–743.
14.EttoRM,CruzLM,JesusEC,etal.Prokaryoticcommunitiesof
acidicpeatlandsfromtheSouthernBrazilianAtlanticForest.
BrazJMicrobiol.2012;43:661–674.
15.MendesLW,TaketaniRG,NavarreteAA,TsaiSM.Shiftsin
phylogeneticdiversityofarchaealcommunitiesinmangrove
sedimentsatdifferentsitesanddepthsinsoutheastern
Brazil.ResMicrobiol.2012;163:366–377.
16.CastroAP,SilvaMRSS,QuirinoBF,BustamanteMMC,Krüger
RH.MicrobialdiversityinCerradobiome(Neotropical
Savanna)soils.PLoSOne.2016;11:e0148785.
17.CastroAAJF,MartinsFR,FernandesAG.Thewoodyfloraof
CerradovegetationintheStateofPiauí,NortheasternBrazil.
EdinbJBot.1998;55:455–472.
18.AraujoASF,BezerraWM,SantosVM,etal.Distinctbacterial
communitiesacrossagradientofvegetationfroma
preservedBrazilianCerrado.AntovanLeeuw.
2017;110:457–469.
19.OliveiraMEA,MartinsFR,CastroAAJF,SantosJR.Classesde
coberturavegetaldoparquenacionaldesetecidades
(transicaocampo-floresta)utilizandoimagensTM/Landsat,
NEdoBrasil.ProceedingsXIIISimposioBrasileirode
SensoriamentoRemotoAnais.2007;13:1775–1783.
20.TedescoMJ,GianelloC,BissaniCA.Analisesdesolosplantase
outrosmateriais.PortoAlegre:UFRGS;1995.
21.CaporasoJG,LauberCL,WaltersWA,etal.Globalpatternsof
16SrRNAdiversityatadepthofmillionsofsequencesper
sample.ProcNatlAcadSciUSA.2011;108:4516–4522.
22.PylroVS,RoeschLFW,OrtegaJM,etal.BrazilianMicrobiome
Project:revealingtheunexploredmicrobialdiversity–
challengesandprospects.MicrobEcol.2014;67:
237–241.
23.DeSantisTZ,HugenholtzP,LarsenN,etal.Greengenes,a
chimera-checked16SrRNAgenedatabaseandworkbench
compatiblewithARB.AppEnvironMicrobiol.
2006;72:5069–5072.
24.AndersonM.Anewmethodfornon-parametricmultivariate
analysisofvariance.AustEcol.2001;26:32–46.
25.HammerØ,HarperDAT,RyanPD.Past:Paleontological
StatisticsSoftwarepackageforeducationanddataanalysis.
26.ParksDH,TysonGW,HugenholtzP,BeikoRG.STAMP:
statisticalanalysisoftaxonomicandfunctionalprofiles.
Bioinformatics.2014;30:3123–3124.
27.WelchBL.Thegeneralizationof“Student’s”problemwhen
severaldifferentpopulationvariancesareinvolved.
Biometrika.1947;34:28–35.
28.BenjaminiY,HochbergY.Controlingthefalsediscoveryrate
–apracticalandpowerfulapproachtomultipletesting.J
RoyalStSoc.1995;57:289–300.
29.GorresC-M,ConradR,PetersenSO.Effectofsoilproperties
andhydrologyonArchaealcommunitycompositioninthree
temperategrasslandsonpeat.FEMSMicrobiolEcol.
2013;85:227–240.
30.MendesLW,TsaiSM,NavarreteAA,HollanderM,vanVeen
JA,KuramaeEE.Soil-bornemicrobiome:linkingdiversityto
function.MicrobEcol.2015;70:255–265.
31.NicolGW,GloverLA,ProsserJI.Molecularanalysisof
methanogenicarchaealcommunitiesinman-agedand
naturaluplandpasturesoils.GlobChangeBiol.
2003;9:1451–1457.
32.NicolGW,TscherkoD,EmbleyTM,ProsserJI.Primary
successionofsoilCrenarchaeotaacrossarecedingglacier
foreland.EnvironMicrobiol.2005;7:337–347.
33.StieglmeierM,MooshammerM,KitzlerB,etal.Aerobic
nitrousoxideproductionthroughN-nitrosatinghybrid
formationinammonia-oxidizingarchaea.ISMEJ.
2014;8:1135–1146.
34.LeiningerS,UrichT,SchloterM,etal.Archaeapredominate
amongammonia-oxidizingprokaryotesinsoils.Nature.
2006;442:806–809.
35.NavarreteAA,TaketaniRG,MendesLW,CannavanFS,
MoreiraFMS,TsaiSM.Land-usesystemsaffectarchaeal
communitystructureandfunctionaldiversityinWestern
Amazonsoils.RevBrasCiSolo.2011;35:
1527–1540.
36.VetrianiC,JannaschJW,MacGregorBJ,StahlDA,Reysenbach
A-L.Populationstructureandphylogeneticcharacterization
ofmarinebenthicarchaeaindeep-seasediments.Appl
EnvironMicrobiol.1999;65:4375–4384.
37.JurgensG,LindströmK,SaanoA.Novelgroupwithinthe
kingdomCrenarchaeotafromborealforestsoil.ApplEnviron
Microbiol.1997;63:3090–3095.
38.IinoT,TamakiH,TamazawaS,etal.Candidatus
Methanogranumcaenicola:anovelmethanogenfromthe
anaerobicdigestedsludge,andproposalof
Methanomassiliicoccaceaefam.nov.and
Methanomassiliicoccalesord.nov.,foramethanogenic
lineageoftheclassThermoplasmata.MicrobEnviron.
2013;28:244–250.
39.TripathiBM,KimM,Lai-HoeA,etal.pHdominatesvariation
intropicalsoilarchaealdiversityandcommunitystructure.
FEMSMicrobiolEcol.2013;86:303–311.
40.Gubry-RanginC,HaiB,QuinceC,etal.Nichespecialization
ofterrestrialarchaealammoniaoxidizers.ProcNatlAcadSci
USA.2011;108:21206–21211.
41.HuH-W,ZhangL-M,YuanC-L,etal.Thelarge-scale
distributionofammoniaoxidizersinpaddysoilsisdrivenby
soilpH,geographicdistance,andclimaticfactors.Front