RevistaBrasileiradeEntomologia63(2019)108–111
REVISTA
BRASILEIRA
DE
Entomologia
AJournalonInsectDiversityandEvolutionw w w . r b e n t o m o l o g i a . c o m
Short
Communication
Sharing
of
termites
(Blattodea:
Isoptera)
between
sugarcane
matrices
and
Atlantic
Forest
fragments
in
Northeast
Brazil
Alane
Ayana
Vieira
de
Oliveira
Couto
a,∗,
Martín
Alejandro
Montes
b,
Rozzanna
Esther
Cavalcanti
Reis
de
Figueirêdo
Chaves
a,
Alexandre
Vasconcellos
aaUniversidadeFederaldaParaíba,DepartamentodeSistemáticaeEcologia,LaboratóriodeTermitologia,JoãoPessoa,PB,Brazil bUniversidadeFederalRuraldePernambuco,DepartamentodeBiologia,Recife,PE,Brazil
a
r
t
i
c
l
e
i
n
f
o
Articlehistory:Received14October2018 Accepted4February2019 Availableonline18February2019 AssociateEditor:M.ElianaCancello Keywords: Conservation Feedinggroups Isolation Speciesdispersal Speciesrichness
a
b
s
t
r
a
c
t
TheAtlanticForestofSouthAmericaisoneofthemostdegradedtropicalforestsandthecultivationof sugarcaneisconsideredoneofthemaincauses.Inhumidforeststermitesstandoutwithregardtotheir abundanceandfunctionalimportance.Thepresentstudyaimedtocomparetermiteassemblagesof frag-mentsoftheAtlanticForestwiththatofthesugarcanematricesthatsurroundthem.Collectionswere performedintwosugarcaneplantationsinNortheastBrazil.IneachplantationafragmentofAtlantic For-estandanadjacentsugarcanefieldweresampledusingastandardizedtermitesamplingprotocol.Atotal of39speciesand302encounterswererecorded.Speciesrichness,relativeabundanceandcomposition differedsignificantlybetweenforestsandthematrices,withthepresenceofexclusivespeciesineach environment—25intheforestsandseveninthematrices.Soilfeedingspeciesofthesubfamily Apicoter-mitinaeandspeciesofopenareaswerefoundinthematrices.Therewasamarkeddifferencebetween theassemblagesofthematrices,possiblyduetosoilcharacteristics.Themajorityofthespeciesfoundin thematricesdonotcausedamagetothecrop,butinsteadactintheprocessesofsoildecompositionand formation,therebycontributingtoincreasedproductivity.
©2019SociedadeBrasileiradeEntomologia.PublishedbyElsevierEditoraLtda.Thisisanopen accessarticleundertheCCBY-NC-NDlicense(http://creativecommons.org/licenses/by-nc-nd/4.0/).
TheAtlanticForestofSouthAmericaisconsideredoneofthe
largest biodiversity repositories on the planet and one of the
mostdegradedtropicalforests(Galindo-Lealand Câmara,2005;
Marchese,2015).ItisestimatedthatthecurrentareaoftheAtlantic
Forestrepresentsjustover 11%of itsoriginalcoverage(Ribeiro
etal.,2009)andsugarcaneisoneofthecropswhoseexpansion
hasbeen identified asa main causeof the current scenario of
degradation.IntheNortheastBrazil,sugarcanematrices
surround-ingremnantsofAtlanticForestcompriseacommonfeatureofthe
landscape(Rantaetal.,1998).Atotalof866.5thousandhectares
ofsugarcanewasharvestedinthisregionin2016/2017(CONAB,
2017).
Inhumidforests,suchastheAtlanticForest,termitesstandout
withregardtotheirabundanceandfunctionalimportance.Theyare
importanteusocialorganismsinthedynamicsoftheecological
pro-cessesrelatedtoenergyflowandthenutrientcyclingofvegetable
necromass(Vasconcellos,2010;Vasconcellos andMoura,2010).
Theconversionofnaturalareastomonoculturesandtheselective
∗ Correspondingauthor.
E-mail:[email protected](A.A.Couto).
cuttingof treesarerecognizedasbeingresponsibleforreduced
speciesrichnessandabundanceoftermites,aswellaschangesin
theproportionoffeedinggroups,withsoilfeedingspecies(feeding
groupsIIIandIVaccordingtotheclassificationofDonovanetal.,
2001)beingthemostsensitivetoenvironmentalchanges(Bandeira
andVasconcellos,2002;Eggletonetal.,1996).
Inthiscontext,theobjectiveofthisstudywastocompare
ter-mite assemblagesof AtlanticForest fragments withthat ofthe
sugarcanematrices that surroundthem, seekingtoevaluate(i)
speciesrichness,relativeabundanceandthecompositionand
dis-tributionoffeedinggroupsinmatricesandforestfragments;and
(ii)thehabitsandpest-status,basedonliteraturerecords,ofthe
termitespecieslivinginthesugarcanematrices.
Theresearchwascarriedoutintwosugarcaneplantationsin
NortheastBrazil.Thefirst,UsinaSãoJoão,islocatedinthe
munici-palityofSantaRita,LitoralCentrooftheParaíbastate(07◦0945.8S,
35◦0351.5W),wherecollectionswerecarriedoutbetween
Octo-ber2014andApril2015.Themeanannualtemperatureis25.2◦C,
themeanrelativehumidityoftheairis83%andannualrainfallis
2193.6mm.Duringthefieldworktherainfallvariedbetween13.3
and40.7mm(INMET,2019).Thesoiloriginatesfromclay-sandy
sedimentsandis classifiedas Red-yellowArgisolwithsandyto
https://doi.org/10.1016/j.rbe.2019.02.001
0085-5626/©2019SociedadeBrasileiradeEntomologia.PublishedbyElsevierEditoraLtda.Thisis anopenaccessarticleundertheCCBY-NC-NDlicense(http:// creativecommons.org/licenses/by-nc-nd/4.0/).
A.A.Couto,M.A.Montes,R.E.Chaves,etal./RevistaBrasileiradeEntomologia63(2019)108–111 109
loamysandytexture,andisdeepandwithlowfertility(Santana,
1987). The vegetation of the forest fragments is classified as
semideciduousseasonalforestcharacterizedbyamixtureof
sec-ondaryAtlanticForestwithisolatedareasofopenCerradocalled
‘tabuleiros’(Rodriguesetal.,2013).Thesecondplantation,Usina
SãoJosé,islocatedinthemunicipalityofIgarassu,MataNorteof
thePernambucostate(7◦497S,35◦0045W),wherecollections
werecarriedoutbetweenSeptember2015andJanuary2016.The
meanannualtemperatureis26.3◦C,themeanrelativehumidityof
theairis83.9%andannualrainfallis1455.6mm.Duringthefield
worktherainfallvariedbetween16.6and91.8mm(INMET,2019).
ThesoiloriginatesfromsedimentsoftheBarreiraGroupandis
clas-sifiedasRed-yellowLatosolwithtexturevaryingfromsandyclay
toclayey,andisdeepandwithlowtomediumfertility(Koffler
etal.,1986).Thevegetationofthestudiedfragmentisclassified
asSemidecidualSeasonalLowlandForest(ThomasandBarbosa,
2008).Thesugarcanevarietycultivatedinthestudyareasofthetwo
plantationswasRB92579.Theareashadnotbeenreceiving
pesti-cidesforatleast18monthsandhadnotexperiencefiresforatleast
sixmonths.
ThecollectionprotocolproposedbyCancelloetal.(2014)was
applied in each area, which consistsof the demarcation of six
65m×2mtransectscontainingfive5m×2mplotsspacedat10m.
The transects were established at least 30m from the
planta-tion/forestborders.Thecollectiontimeateachplotcorresponds
toasamplingeffortof1hourbyperson.Duringthistime,termites
weresearchedforinallpossiblemicrohabitatsandthenspecimens
werecollectedforspeciesidentificationandclassificationby
feed-inggroupaccordingtotheproposalofDonovanetal.(2001).This
protocolwasoriginallydevelopedforthecollectionoftermitesin
tropicalforests,buthassincebeenappliedinopenecosystemssuch
asCaatinga(Vasconcellosetal.,2010;Vianaetal.,2014).Voucher
materialwasdepositedintheColec¸ãodeIsopteraofUniversidade
FederaldaParaíba.Theobservedspeciesrichnessandnumberof
encounterswereobtainedforeachforestfragmentandsugarcane
area,thelatterofwhichwasusedasanindicatorofrelative
abun-dance(Cancelloetal.,2014).
Assemblageswereorderedusingnon-metricmultidimensional
scaling(nMDS)withJaccardsimilarity.Differencesinthe
compo-sitionofspeciesandfeedinggroupsbetweenforestandadjacent
Table1
Observedspeciesrichness,numberofencountersandfeedinggroupinAtlanticforestfragmentsandsugarcanefieldsinNortheastBrazil.N,numberofplotsinwhicha specieswasencountered;Sobs,observedrichness;Us.,Usina.AF,AtlanticForest;S,sugarcanefield;FG,feedinggroup.
Family/subfamily/species Us.SãoJoão Us.SãoJosé
NAF NS NAF NS FG
Rhinotermitidae
Heterotermeslongiceps(Snyder,1924) 4 – 3 – I
Termitidae Apicotermitinae Apicotermitinaesp.1 – – 1 – III Apicotermitinaesp.2 – – 2 – III Apicotermitinaesp.3 – – – 1 III Apicotermitinaesp.4 – – – 1 III Anoplotermessp.1 – – 16 – III Anoplotermessp.2 10 – 5 9 III Anoplotermessp.3 1 – 8 2 III Aparatermessp.1 – – – 4 III Aparatermessp.2 1 – – – III Aparatermessp.3 – – – 4 III Grigiotermessp. 1 – 1 – IV Tetimatermessp. – – 1 – IV Nasutitermitinae Atlantitermessp. 1 – – – IV
Diversitermesdiversimiles(Silvestri,1901) 6 – 3 – II
Nasutitermescallimorphus(Mathews,1977) 10 – 10 – II
Nasutitermescorniger(Motschulsky,1855) 7 – 8 – II
Nasutitermescoxipoensis(Holmgren,1910) – – – 10 II
Nasutitermesephratae(Holmgren,1910) – – 10 – II
NasutitermesgaigeiEmerson,1925 – – 2 – II
Nasutitermesjaraguae(Holmgren,1910) 1 – – – II
Nasutitermesmacrocephalus(Silvestri,1903) 2 – – – II
Nasutitermesobscurus(Holmgren,1906) 3 – – – II
Nasutitermessp. – – 1 – II
Velocitermesvelox(Holmgren,1906) 1 – 4 – II
Syntermitinae
Embiratermesneotenicus(Holmgren,1906) 6 – – – II
EmbiratermesparvirostrisConstantino,1993 7 – – – III
Labiotermeslabralis(Holmgren1906) 7 – 4 – IV
Silvestritermesholmgreni(Snyder,1926) 3 – 3 – II
Syntermesgrandis(Rambur,1842) – – – 4 II
SyntermesnanusConstantino,1995 – – – 2 II
Termitinae
AmitermesamiferSilvestri,1901 7 2 1 – II
AmitermesnordestinusMélo&Fontes2003 – 16 – – II
Cavitermestuberosus(Emerson,1925) 1 – 1 – III
CylindrotermessapirangaRocha&Cancello,2007 1 18 – 4 II
MicrocerotermesindistinctusMathews,1977 23 – 15 1 II
NeocapritermesopacusHagen,1858 2 – 2 14 III
Orthognathotermessp. 1 – – – IV
TermesmedioculatusEmerson,1949 3 – – – III
Sobs 24 3 21 12
110 A.A.Couto,M.A.Montes,R.E.Chaves,etal./RevistaBrasileiradeEntomologia63(2019)108–111 0.2 0.0 -0.2 -0.2 -0.4 -0.2 0.0 0.2 -0.2-0.1 -0.1 0.0 0.0 0.1 0.1 0.2 0.2 0.3 Stress:0.11 Stress:0.28 nMDS axis 1 nMDS axis 2 nMDS axis 2 nMDS axis 1
A
B
Fig.1.Non-metricmultidimensionalscalingfortermiteassemblagesoftwoAtlantic Forestfragmentsandadjacentsugarcaneplantations.UsinasãoJoão(A)andUsina SãoJosé(B).䊉,AtlanticForest.,sugarcanefield.
24 20 16 12 8 4 20 40 IV III II I 60 80 100 120 Number of encounters Species r ichness 0 AF AF AF AF
Us. São João Us. São José Us. São João Us. São José
S S S S
0
A
B
Fig.2.Speciesrichness(A)andnumberoftermiteencounters(B)perfoodgroupof twoAtlanticForestfragmentsandadjacentsugarcanefieldsoftwoplantationsin NortheastBrazil.Us.,Usina;AF,AtlanticForest;S,sugarcanefield;I,feedinggroupI; II,feedinggroupII;III,feedinggroupIII;IV,feedinggroupIV(Donovanetal.,2001).
matrixweretestedthroughnon-parametricpermutationanalysis
ofvariance(PERMANOVA)with9999permutations.Allofthese
analyseswereperformedusingPASTv.3.20 software(Hammer
andHarper,2006).
Atotalof39speciesand302encounterswererecorded,with31
speciesand210encountersrecordedfortheAtlanticForest
frag-ments,14 speciesand 92encountersin thesugarcaneareas. In
UsinaSãoJoão(fragment+matrix)wererecorded25speciesand
145encounters(Table1).Atotalof109encountersand24species
wererecordedintheAtlanticForestfragment,22ofwhichwere
exclusivetothisenvironment,while36encountersandonlythree
specieswererecordedin thesugarcanematrix,withAmitermes
nordestinusSilvestri,1901,beingexclusivetothisenvironment.In
UsinaSãoJosé(fragment+matrix),29speciesand157encounters
wererecorded(Table1).Atotalof101encountersand21species
wererecordedintheAtlanticForestfragment,ofwhich17were
exclusivetothisenvironment,while56encountersand12species
wererecordedinthesugarcanematrix,eightofwhichwere
exclu-sivetothisenvironment.
ThenMDSindicatedthatthestructure oftheassemblagesof
theforestfragmentandthematrixdifferedinthebothplantations
(Fig.1).ThePERMANOVAshowedthatthespeciescomposition
dif-feredsignificantlyinthetwoplantformations,bothforUsinaSão
João(F=20.2,p<0.05),andforUsinaSãoJosé(F=9.93,p<0.05).
TheAtlanticForestfragmentshadsimilarresultsregardingthe
structureofthefeedinggroups,withagreaternumberofspecies
andencountersrecordedforfeedinggroupII,followedbyfeeding
groupsIII,IVandI.However,inthematrixofUsinaSãoJoãoonly
feedinggroupIIwasrecorded,whileinthematrixofUsinaSãoJosé
feedinggroupsIIandIIIwererecorded(Fig.2).
Thisis thefirstrecordofspecies belongingtothesubfamily
ApicotermitinaeinsugarcanefieldsinNortheastBrazil.Thereis
arecordofthissubfamilyintheSoutheastBrazil,butthespecies
wasonlyidentifiedtothesubfamilylevel(Junqueiraetal.,2015).
AllofthespeciesfoundinsugarcanefieldsofUsinaSãoJoãobelong
togenerathatwerepreviouslyassociatedwithsugarcaneinthe
NortheastBrazil(Guagliumi,1972/73;NovarettiandFontes,1998;
Mirandaetal.,2004).
InUsina SãoJoão,thespeciesrichness oftheAtlanticForest
fragmentwaseighttimesgreaterthanthatrecordedinthe
sugar-canefield,whileinUsinaSãoJoséthespeciesrichnessintheforest
fragmentwasapproximately1.7timesgreater.Itisimportantto
notethattheassemblagesfoundinthematricesdonotcorrespond
exactlytoasubgroupoftheassemblagesfoundin theadjacent
forestfragments,andpossessaconsiderablenumberofexclusive
species,which,onalandscapescale,representsanincreaseintotal
speciesrichness.Otherstudiescomparingassemblagesoftermites
betweenforestfragmentsandnearbyplantationsalsorecordeda
decreaseinspeciesrichnessandabundance,aswellasdifferences
intaxonomicandfeedinggroupcomposition(Attignonetal.,2005;
Bassetetal.,2016;Eggletonetal.,1996).Anotherfactorthatmay
havecontributedtothedecreaseintermitespeciesrichnessinthe
sugarcanematrixisthetypeofmanagementperformed.The
prac-ticeofpreharvestburningisstillcommoninsugarcanecultivation
andreducestheamountoforganicmatterinthesoilcomparedto
greenormechanizedharvest,aswellassignificantlyreducingthe
abundanceofarthropods(Sajjadetal.,2012;Wiedenfeld,2009).
Thelowerspeciesrichnessandabundance, coupledwiththe
simplificationofthestructureofthefeedinggroups,inthematrices
inrelationtothoserecordedintheAtlanticForestfragments
indi-catesthatthematrixfunctionsasafilterforthegreatmajorityof
speciesbutfavorsthepermanenceofotherpopulations,especially
species of openareas suchas Amitermes nordestinus,
Nasutiter-mes coxipoensis (Holmgren, 1910), Syntermes grandis (Rambur,
1842)andSyntermesnanusConstantino,1995(Alvesetal.,2011;
Constantino,1995;Cunha andMorais,2010;Garcia etal.,2006; Mathews,1977).
InthesugarcanefieldofUsinaSãoJoão,allofthespecieswere
includedinfeedinggroupII,whileinthesugarcanefieldofUsina
SãoJosé,ofthe12speciesrecorded,sixofthesubfamily
Apicoter-mitinaeand thespecies Neocapritermesopacus (Termitinae)are
includedinfeedinggroupIII.ThespeciesS.grandisandS.nanus,
despitebeinginfeedinggroupII,haveastrongconnectionwith
thesoilsincetheirnestsaresubterranean(Constantino,1995).
Thespeciescompositionsofthetwosugarcanefieldswerequite
different.Thisdifferencemayberelatedtoagreateramountof
clayinthesoilofUsinaSãoJosé(seethedescriptionoftheareas).
Clayis akeycomponent forensuringstructuralstability of
ter-mitenests(Jouquetetal.,2004).Therefore,sandysoilsmakenest
buildingdifficult and decreasegallery stability (Lee and Wood,
1971).ThetermiteassemblagesoftworestingaareasintheParaíba
state,whosesoiltextureresemblesthatofthesoiloftheUsinaSão
Joãosugarcanefield,hadalowoccurrenceofspeciesofthe
sub-familyApicotermitinae,whichwasassociatedwithsoilproperties
(Vasconcellosetal.,2005).Thus,thedifferencesfoundindicatethat
evenmatricesformedbythesamemonoculture,includingthesame
varietyofsugarcaneandmanagementpractices,cansupportvery
differentassemblages.
Althoughtermitesareconsideredimportantpestsofthe
sug-arcane crop in Northeast Brazil (Novaretti and Fontes, 1998),
publications thatstudytermiteassemblages insugarcanefields
inthisregionaregenerallyscarceandrelativelyold(Guagliumi,
1972/73;Mirandaetal.,2004;NovarettiandFontes,1998).Inthe
presentresearch,thespeciesS.grandisandS.nanuswereobserved
damagingtheleavesofplantsstillindevelopment,whiletheother
specieswerenotobservedcausinginjuriestotheplantsandwere
feedingonstrawororganicmatterinthesuperficiallayersofthe
soil,thuscontributingtotheprocessofnutrientcycling.
Thereisadrasticsimplificationofthetaxonomicandfunctional
structuresoftermiteswiththeconversionofAtlanticForestinto
sugarcanefield.Ontheotherhand,thematrixisnotacompletely
inhospitableenvironmentforthepresenceoftermitesandisable
tomaintainspecies that arenot foundin theadjacentAtlantic
Appar-A.A.Couto,M.A.Montes,R.E.Chaves,etal./RevistaBrasileiradeEntomologia63(2019)108–111 111
ently,mostofthespeciesfoundinthematrixdonotdamagethe
crop,andinsteadfeedonstrawandorganicmattercontainedinthe
superficiallayersofthesoil,thuscontributingtonutrientcycling.
Variationinsoiltype,especiallytheamountofclay,ofthesame
monocultureapparentlycaninfluencethecompositionoftermite
assemblages,andalterthepermeabilityofthematrix.
Conflictsofinterest
Theauthorsdeclarenoconflictsofinterest.
Acknowledgements
TheauthorsthankUsinaSãoJoãoandUsinaSãoJoséfor
autho-rizingthefieldactivitiesintheirfacilitiesandthetraineesofthe
termitologylaboratoriesofUFPBandUFRPEforassistanceduring
fieldactivities.
References
Alves,W.deF.,Mota,A.,Lima,R.de,Bellezoni,R.,Vasconcellos,A.,2011.Termites asbioindicatorsofhabitatqualityintheCaatingaBrazil:isthereagreement betweenstructuralhabitatvariablesandthesampledassemblages?Neotrop. Entomol.40,39–46.
Attignon,S.E.,Lachat,T.,Sinsin,B.,Nagel,P.,Peveling,R.,2005.Termiteassemblages inaWest-Africansemi-deciduousforestandteakplantations.Agric.Ecosyst. Environ.110,318–326.
Bandeira,A.G.,Vasconcellos,A.,2002.Quantitativesurveyoftermitesinagradient ofdisturbedhighlandforestinnortheasternBrazil(Isoptera).Sociobiology39, 429–439.
Basset, Y.,Barrios,H., Ramirez,J.A., Lopez,Y., Coronado,J., Perez, F.,Arizala, S.,Bodadilla,R.,Leponce,M.,2016.Contrastingthedistribution of butter-fliesandtermitesinplantationsandtropicalforests.Biodivers.Conserv.26, 151–176.
Cancello,E.M.,Silva,R.R.,Vasconcellos,A.,Reis,Y.T.,Oliveira,L.M.,2014.Latitudinal variationintermitespeciesrichnessandabundancealongtheBrazilianAtlantic Foresthotspot.Biotropica46,441–450.
CONAB,CompaniaNacionaldeAbastecimento,2017.Acompanhamentodasafra brasileiradecana-de-ac¸úcar1.
Constantino,R.,1995.RevisionoftheneotropicaltermitegenusSyntermes Holm-gren(Isoptera:Termitidae).Dept.Entomol.Univ.Kansas55,455–518. Cunha, H.F., Morais, P.P.A.M., 2010. Relac¸ão espécie-área em cupinzeiros de
pastagem,Goiânia-GO,Brasil.EntomoBrasilis3,60–63.
Donovan,S.E.,Eggleton,P.,Bignell,D.E.,2001.Gutcontentanalysisandanewfeeding groupclassificationoftermites.Ecol.Entomol.26,356–366.
Eggleton, P., Bignell, D.E., Sands, W.A., Mawdsley, N.A., Lawton, J.H., Wood, T.G., Bignell, N.C., 1996. The diversity, abundance and biomass of ter-mites under differing levels of disturbance in the Mbalmayo Forest Reserve,southernCameroon.Philos.Trans.R. Soc.LondonBBiol.Sci.351, 51–68.
Galindo-Leal,C.,Câmara,I.G.,2005.StatusdohotspotMataAtlântica:umasíntese. In:MataAtlâNtica:Biodiversidade,Ameac¸asePerspectivas.
Garcia,J.,Maekawa,K.,Constantino,R.,Matsumoto,T.,Miura,T.,2006.Analysisofthe geneticdiversityofNasutitermescoxipensis(Isoptera:Termitidae)innatural fragmentsofBrazilianCerradousingAFLPmarkers.Sociobiology.
Guagliumi,P.,n.d.Pragasdacana-de-ac¸úcarnonordestedoBrasil. Hammer,Ø.,Harper,D.A.T.,2006.PaleontologicalDataAnalysis.
INMET – Instituto Nacional de Meteorologia, 2019. Banco de Dados Mete-orológicos para Ensino e Pesquisa[WWW Document],http://www.inmet. gov.br/portal/index.php?r=bdmep/bdmep(accessed01.02.19).
Jouquet,P.,Tessier,D.,Lepage,M.,2004.Thesoilstructuralstabilityoftermitenests: roleofclaysinMacrotermesbellicosus(IsopteraMacrotermitinae)moundsoils. Eur.J.SoilBiol.40,23–29.
Junqueira,L.K.,Gonc¸alves,E.R.,Teixeira,L.M.C.,2015.Termitecommunitiesin sugar-caneplantationsinSoutheasternBrazil:anecologicalapproach.EntomoBrasilis 8,105–116.
Koffler,N.P.,Lima,J.F.W.F.,Lacerda,J.F.,Santana,J.F.,Silva,M.A.,1986.Caracterizac¸ão Edafo-climáticadasRegiõesCanavieirasdoBrasil:Pernambuco.In: PLANALSU-CAR,Piracicaba.
Lee,K.E.,Wood,T.G.,1971.TermitesandSoils.
Marchese,C.,2015.Biodiversityhotspots:ashortcutforamorecomplicatedconcept. Glob.Ecol.Conserv.3,297–309.
Mathews,A.G.,1977.Studies onTermites fromtheMatoGrosso StateBrazil. AcademiaBrasileiradeCiências.
Miranda,C.S.,Vasconcellos,A.,Bandeira,A.G.,2004.Termitesinsugarcanein North-eastBrazil:ecologicalaspectsandpeststatus.Neotrop.Entomol.33,237–241. Novaretti,W.R.T.,Fontes,L.R.,1998.Cupins:Umagraveameac¸aàcana-de-ac¸úcar
noNordestedoBrasil.In:Cupins:ODesafioDoConhecimento,p.512. Ranta,P.,Blom,T.O.M.,Niemela,J.,Joensuu,E.,Siitonen,M.,1998.Thefragmented
AtlanticrainforestofBrazil:size,shapeanddistributionofforestfragments. Biodivers.Conserv.7,385–403.
Ribeiro,M.C.,Metzger,J.P.,Martensen,A.C.,Ponzoni,F.J.,Hirota,M.M.,2009.The BrazilianAtlanticForest:howmuchisleft,andhowistheremainingforest distributed?Implicationsforconservation.Biol.Conserv.142,1141–1153. Rodrigues,R.,Gustavo,F.,Franc¸a,R.,Mesquita,D.O.,2013.Recordoftheoccurrence
ofLachesismuta(Serpentes,Viperidae)inanAtlanticForestfragmentinParaíba Brazil,withcommentsonthespecies’preservationstatus.Capa26,283–286. Sajjad,A.,Ahmad,F.,Makhdoom,A.H.,Imran,A.,2012.Doestrashburningharm
arthropodsbiodiversityinsugarcane?Int.J.Agric.Biol.14,1021–1023. Santana,J.F.,1987.Caracterizac¸ãoEdafo-climáticadasRegiõesCanavieirasdoBrasil:
Paraíba.
Thomas,W.W.,Barbosa,M.R.V.,2008.NaturalvegetationtypesintheAtlanticcoastal forestofNortheasternBrazil.MemoirsoftheNewYorkBotanicalGarden. Vasconcellos,A.,2010.Biomassandabundanceoftermitesinthreeremnantareas
ofAtlanticForestinnortheasternBrazil.Rev.Bras.Entomol.54,455–461. Vasconcellos, A.,Bandeira, A.G.,Moura, F.M.S.,Araújo, V.F.P.,Gusmão,M.A.B.,
Constantino,R.,2010.Termiteassemblagesinthreehabitatsunderdifferent disturbanceregimesinthesemi-aridCaatingaofNEBrazil.J.AridEnviron.74, 298–302.
Vasconcellos,A.,Mélo,A.C.,Segundo,E.M.,Bandeira,A.,2005.Cupinsdeduas flo-restasderestingadonordestebrasileiro,Iheringia.SérieZool.95,127–131. Vasconcellos,A.,Moura,F.M.D.S.,2010.Woodlitterconsumptionbythreespeciesof
NasutitermestermitesinanareaoftheAtlanticCoastalForestinnortheastern Brazil.J.InsectSci.10,72.
Viana,A.B.,Souza,V.B.,Reis,Y.T.,Marques-Costa,A.P.,2014.Termiteassemblages indrytropicalforestsofNortheasternBrazil:aretermitesbioindicatorsof envi-ronmentaldisturbances?Sociobiology61,324–331.
Wiedenfeld,B.,2009.Effectsofgreenharvestingvsburningonsoilproperties, growthandyieldofsugarcaneinsouthTexas.J.Am.Soc.SugarCaneTechnol. 29,102–109.