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Natureza
&
Conservação
Brazilian
Journal
of
Nature
Conservation
SupportedbyBoticárioGroupFoundationforNatureProtection
Policy
Forums
Environmental
licensing
on
rhodolith
beds:
insights
from
a
worm
Cinthya
Simone
Gomes
Santos
a,
Jaqueline
Barreto
Lino
b,
Priscila
de
Cerqueira
Veras
b,c,
Gilberto
Menezes
Amado-Filho
d,
Ronaldo
Bastos
Francini-Filho
e,
Fabio
Santos
Motta
b,
Rodrigo
Leão
de
Moura
f,
Guilherme
Henrique
Pereira-Filho
b,∗aDepartmentofMarineBiology,InstituteofBiology,UniversidadeFederalFluminense,Niterói,RJ,Brazil
bInstitutodoMar,LaboratoryofMarineEcologyandConservation,UniversidadeFederaldeSãoPaulo,Santos,SP,Brazil cCenterforNaturalandHumanSciences,UniversidadeFederaldoABC,SãoBernardodoCampo,SP,Brazil
dInstitutodePesquisasJardimBotânicodoRiodeJaneiro,RiodeJaneiro,RJ,Brazil
eDepartmentofEngineeringandEnvironment,UniversidadeFederaldaParaíba,RioTinto,PB,Brazil
fInstituteofBiology,LaboratóriodeSistemasAvanc¸adosdeGestãodaProduc¸ão(SAGE),InstitutoAlbertoLuizCoimbrade
Pós-Graduac¸ãoePesquisadeEngenharia(COPPE),UniversidadeFederaldoRiodeJaneiro,RiodeJaneiro,RJ,Brazil
a
r
t
i
c
l
e
i
n
f
o
Articlehistory:
Received12January2016
Accepted7June2016
Availableonline1July2016
Keywords:
Marinediversity
Maerl
Mesophoticreefs
Crustosecorallinealgae
a
b
s
t
r
a
c
t
Rhodolithsarefree-livingnodulesformedbycrustosecorallinealgaethatpromote
multi-dimensionalmicrohabitatsforahighlydiversecommunity.BecausetheirCaCO3production,
rhodolithbedsconstituteareasofinterestforminingactivities.Ontheotherhand,other
goodsandservicesprovidedbytheseenvironmentssuchasnurserieshabitats,fishingand
climateregulationremainundersized.BesidesdirectlyCaCO3exploitation,thesediverse
ecosystemswithintheBrazilianeconomicexclusivezoneareoftencoveringpotentiallysites
foroilandgasextraction.TheIBAMA(EnvironmentalAgencyoftheBraziliangovernment)
havebeenapplyingtheprecautionaryprincipletodenyrequestsforoil/gasdrillingactivities
whererhodolithbedsoccur.Here,wediscussrecentdataaboutdiversityassociatedwith
rhodolithsandalsorecordthe“rare”wormNuchalosylliscf.maiteae.Morethanthe
distribu-tionofoneonlyspecies,ourfindingisanemblematicexampleofourinfancyknowledge
stateaboutdiversityassociatedwithrhodolithbedsinsouthwesternAtlantic.Wearguethat
theseknowledgeisstillinsufficienttosubsideanyattemptinclassifyprioritiesareasfor
oilwellsdrilling.Inaddition,weclaimthattheprecautionaryprincipleadoptedbyIBAMA
mustprevalenceuntilwehaverobustdataallowingpredictionsconcerninghigherorlower
biodiversityassociatedwithrhodolithbeds.
©2016Associac¸ ˜aoBrasileiradeCi ˆenciaEcol ´ogicaeConservac¸ ˜ao.PublishedbyElsevier
EditoraLtda.ThisisanopenaccessarticleundertheCCBY-NC-NDlicense(http://
creativecommons.org/licenses/by-nc-nd/4.0/).
∗ Correspondingauthor.
E-mailaddress:pereira.filho@unifesp.br(G.H.Pereira-Filho).
http://dx.doi.org/10.1016/j.ncon.2016.06.002
1679-0073/©2016Associac¸ ˜aoBrasileiradeCi ˆenciaEcol ´ogicaeConservac¸ ˜ao.PublishedbyElsevierEditoraLtda.Thisisanopenaccess
bycrustose corallinealgae.Theyoccurworldwideandmay
formlargebedsthatcoverhugeexpanseoftropical,
temper-ate,andevenpolarshelves,providingmulti-dimensionalhard
microhabitatsfordiversebiologicalcommunities(Fosteretal.,
2013).BecauseoftheirhugeCaCO3accumulation,rhodolith
bedsconstituteareasofgreatinterestforcarbonates’mining
thatsuppliesagriculturalandindustrialapplications
(Amado-Filhoetal.,2012a;Mouraetal.,2013).Whilerhodolithbeds
are largely and mistakenly seen as mineral resources, the
ecosystem services they provide, such as fishing and
cli-mate regulation, are grossly underrated in environmental
impact assessments(Amado-Filho and Pereira-Filho, 2012).
In Brazil, the country with the world’s largest rhodolith
beds,extractionofup to18t/companyyear−1 may be
regu-larlylicensedbyIBAMA,theFederalEnvironmentalLicensing
Agency (Instruc¸ão Normativa 89, Feb. 02, 2006). Although
sub-surfacerhodolithsare oftenaliveanddefinitelyharbor
high marine biodiversity, the Brazilian law refers to them
asnon-livingmarineresources,withexploratoryregulations
established by the National Mining Department
(Departa-mento Nacionalde Produc¸ão Mineral– DNPDM).Moreover,
rhodolithbedsoverlapwithseveraloilandgasfieldswithin
the Brazilian Economic Exclusive Zone (EEZ). The
build-ing of new infrastructurein such areas has been recently
restrictedbyIBAMA,basedonthePrecautionaryPrinciple–
afundamentaltoolforcounteringthechronicoverlookof
sci-entificuncertaintiesinanunscientificmanner(Cooney,2004).
A
N
Brazil
S3º48’20” 100m50m 20m S3º52’20” W32º27’10” W32º23’10”B
C
Fig.1–SamplinglocalitiesforallknownspecimensofNuchalosyllis.(A)FernandodeNoronhaArchipelago(detail).Light brownpatchesindicateareaswhererhodolithbedshavebeenmapped(Gherardi,2004;Pascellietal.,2013;Amado-Filho etal.,2007;Amado-Filhoetal.,2010;Villas-Boasetal.,2013;Pereira-Filhoetal.,2012;Amado-Filhoetal.,2012a;Bahia etal.,2010;Riuletal.,2009;TestaandBosence,1999;Amado-Filhoetal.,2012b,respectivelyfromsouthtonorth).Blue arrowsindicatelocalitiesofthetwoknownNuchalosyllisspecies,(FukudaandNogueira,2012;RullierandAmoureux,1979). DarkgreenarrowindicatesthesitewherewesampledNuchalosyllisat40mdepth.(BandC)Detailofrhodolithbed(Photos: ZairaMatheus).
etal.,2010;Bahiaetal.,2010;Brasileiroetal.,2015),
knowl-edgeaboutthedistributionandbiodiversityassociatedwith
rhodolithbeds inBrazil isstillfragmentedand incomplete,
impedingthoroughenvironmentalimpactassessmentsofthe
steadilygrowingindustrialactivities.Paradoxically,
uncertain-tiesinpredictingenvironmentalimpactshavebeenevoqued
byeconomicgroupsasareasonfortheapprovalofmining
licenses(Cooney,2004).Oncerhodolithbedscoverextensive
areas ofthe BrazilianEEZ (Fig.1A),large-scale mining and
hydrocarbon’s exploitation are indeed an imminent threat
withyetunpredictableconsequences.Here,whilerecording
theoccurrenceofthe“raregenus”Nuchalosyllis(Polychaeta)in
theFernandodeNoronhaArchipelago(FNA),weemphasize
themajorknowledgegapsaboutthebiodiversityassociated
toBrazilianrhodolithbeds,andtheconsequencesfor
envi-ronmentallicensing.
Beforeourfind(Fig.1)(specimendepositedinMNRJP785),
Nuchalosyllismaiteaewasonlyknownfortheholotype(MZUSP
01016)collected at75mdepthoffshoreRiodeJaneiroState
(Fukuda and Nogueira, 2012). Suchas other known specie
of the same genus, N. maiteae was initially obtained by
ship-based dredgingand grabbing. Despite being the tools
used to provide most of the currently available biological
data about rhodolith-associated biodiversity (Foster et al.,
2013),dredgingandgrabbingarelimitedforsamplingsmall
invertebrates within rhodoliths’ microhabitats, especially
Fig.2–Nuchalosylliscf.maiteae.(A)Anteriorend,dorsalview.(B)Parapodia15,posteriorview;(C)detailofdorsalcirriwith darkredinclusions;(D)Chaetaeheterogomphfalcigerfromparapodia15;(E)Chaetaeheterogomphfalcigerfromparapodia 41;(F)parapodia41,posteriorview,dorsalcirrilost;(G)dorsalcirrophorewithpapillae.Papillae.Legends:ac.,Acicula;cp., Cirrophore;pa.,Papillae;pc.,Peristomialcirri;vc.,Ventralcirri.Scale:A.0.8mm;B.0.13mm;C.0.25mm;D.0.03mm;E. 0.03mm;F.0.1mm;G.0.08mm.
significantrolesinfoodweb(Fosteretal.,2013;Kenchington
and Hutchings, 2012).Only recentlythe use ofSCUBA has
been recognized and established as a complimentary tool
forsamplingsuchsoft-bodiedinfaunalspecies(Fosteretal.,
2013).Forexample,SCUBA-basedassessmentsinCalifornia,
USA, revealed eight species of cryptofaunal chitons, four
ofwhich were previouslyundescribed (Clark, 2000).Santos
etal.(2011)alsousedSCUBAtosamplehoneycombworms
(Polychaeta:Sabellariidae),findingthatsixofthetenSabellaria
rodoliths.
Despitetheaforementionedvalueforcomprehensive
bio-diversityassessments,SCUBA recreational standards limits
sampling to <30m depths. Recently, we used mixed-gas
(TRIMIX)andtechnicaldivingtechniquestosamplerhodolith
bedsinscatteredcontinentalandoceaniclocalitiesalongthe
Brazilian coast (e.g. Pereira-Filho et al., 2012; Moura et al.,
2013;Amado-Filho etal., 2016).Althoughwesampled only
onespecimenofN.cf.maiteaeintheFernandodeNoronha
Archipelago (i.e.; >2000km from the type and onlyknown
locality)(Figs. 1 and 2), it ispossible to hypothesizedthat
thedistributionofthistaxonismuchwiderthanpreviously
known,andthatsamplingeffortisinsufficienttoany
com-prehensiveunderstandingaboutthebiodiversityharboredby
thishabitat.Morethananadditionalrangeextensionrecord
foroneofhundredsofthousands“worm”species,N.maiteae
isanemblematicexampleoftheincipientknowledgeabout
the biodiversity of Southwestern Atlantic rhodolith beds.
Conversely,researchanddiscoveryofhydrocarbon
exploita-tion fields rapidly increased in the last decade, especially
inthemesophotichabitatsofthis region(e.g.,Mouraetal.,
2013), many of those in rhodolith beds such as Peregrino
oilfield,CamposBasin(Tâmegaetal.,2013,2014),thearea
whereN.maiteaewasdiscovered.Offshoredrillingincreases
theconcentrationofsuspendedparticles(Patin,1999),with
well-establishednegativeeffectsoverthehealthofcrustose
coralline algae (e.g., Reynier et al., 2015) and
community-widechangesfromsedimentationandcontamination(Patin,
1999).
Theterm“rarespecies”isassociatedtolowfrequencyand
smallpopulationsizes(Caoetal.,1998).Evenonlytwo
speci-mensofN.maiteaehavebeenfounduptodate;thesampling
effortistoolimitedtoclassifyitoranyotherassociatedspecies
asrareorabundant.Basicinformationaboutpredictor
vari-ablesofassociatedbiodiversityisstilllacking(e.g.;rhodolith
size,volume,form,complexityanddensity).Rhodolithbeds
are extensive and heterogeneous habitats, and the small
spatial scales within the nodules representand additional
challenge fordesigning comprehensivesampling programs
to assess biodiversity patterns. However, considering the
increased rates of anthropogenic disturbances (Broderick,
2015),itisclearthatthetimingneededforextensivesampling
isnotcompatiblewiththespeedatwhichimportant
manage-mentdecisionsneedtobetaken(KenchingtonandHutchings,
2012).
Whilerobustdataon species’occurrencesand
distribu-tion patterns accumulate, and surrogates for biodiversity
patterns are developed(Kenchingtonand Hutchings, 2012),
the precautionary principle adopted by IBAMA must be
consistently appliedin order tosafeguard biodiversityand
ecosystemservicesprovidedbyrhodolithbeds,asevidenced
fromrecentdataaboutmacroalgae(Amado-Filhoand
Pereira-Filho, 2012), fishes (Simon et al., 2016)and the polychaete
worm,N.maiteaerecordedherein.InsteadofpressingIBAMA
for rapid licensing, the industries that affect rhodoliths
andothermegadiversityBrazilianmarineecosystemsmust,
truly, engage in research and conservation initiatives that
go beyondthe immediate needs ofindividual exploitation
projects.
Conflicts
of
interest
Theauthorsdeclarenoconflictsofinterest.
Acknowledgments
We thankthe Fernando de Noronha Marine National Park
staffforlogisticsupportandresearchpermits
(SISBIO/34245-3).FinancialsupportwasprovidedbytheBrazilianResearch
Council (CNPq; grant 484875/2011-6 to GHPF). GMAF, RBFF
andRLMacknowledgegrantsfromCNPq,CAPES,FAPERJand
Brasoil. PCV and JBL acknowledge their scholarships from
Fundac¸ão de Amparo à Pesquisa do Estado de São Paulo
(FAPESP, processes 2013/26594-4 and 2015/15212-9,
respec-tively).
r
e
f
e
r
e
n
c
e
s
Amado-Filho,G.M.,Maneveldt,G.,Manso,R.C.C.,etal.,2007.
Structureofrhodolithbedsfromadepthgradientof4to
55metersatthesouthofEspíritoSantoStatecoast,Brazil.
Cienc.Marinas33,399–410.
Amado-Filho,G.M.,Maneveldt,G.W.,Pereira-Filho,G.H.,etal.,
2010.SeaweeddiversityassociatedwithaBraziliantropical
rhodolithbed.Cienc.Marinas36,371–391.
Amado-Filho,G.M.,Pereira-Filho,G.H.,2012.Rhodolithbedsin
Brazil:anewpotentialhabitatformarinebioprospection.Rev.
Bras.Farmacogn.22,782–788.
Amado-Filho,G.M.,Moura,R.L.,Bastos,A.C.,etal.,2012a.
RhodolithAbedsaremajorCaCO3bio-factoriesinthetropical
SouthWestAtlantic.PLoSONE7,e35171.
Amado-Filho,G.M.,Pereira-Filho,G.H.,Bahia,R.G.,etal.,2012b.
Occurrenceanddistributionofrhodolithbedsonthe
FernandodeNoronhaArchipelagoofBrazil.Aquat.Bot.101,
41–45.
Amado-Filho,G.M.,Moura,R.L.,Bastos,A.C.,etal.,2016.
MesophoticecosystemsoftheuniqueSouthAtlanticatollare
composedbyrhodolithbedsandscatteredconsolidatedreefs.
Mar.Biodivers.,http://dx.doi.org/10.1007/s12526-015-0441-6.
Bahia,R.G.,Abrantes,D.P.,Brasileiro,P.S.,etal.,2010.Rhodolith
bedstructurealongadepthgradientfromnortherncoastof
BahiaState,Brazil.Braz.J.Oceanogr.58,323–337.
Brasileiro,P.S.,Pereira-Filho,G.H.,Bahia,R.G.,etal.,2015.
Macroalgalcompositionandcommunitystructureofthe
largestrhodolitintheworld.Mar.Biodivers.,1–14.
Broderick,A.C.,2015.Grandchallengesinmarineconservation
andsustainableuse.Front.Mar.Sci.2(11),1–13.
Cao,Y.,Williams,D.,Williams,N.E.,1998.Howimportantarerare
speciesinaquaticcommunityecologyandbioassessment?
Limnol.Oceanogr.43,1403–1409.
Clark,R.N.,2000.ThechitonfaunaoftheGulfofCalifornia
rhodolithbeds(withdescriptionsoffournewspecies).
Nemouria–OccasionalPapersoftheDelawareMuseumof
NaturalHistory43,1–20.
Cooney,R.,2004.ThePrecautionaryPrincipleinBiodiversity
ConservationandNaturalResourceManagement:AnIssues
PaperforPolicy-makers,ResearchersandPractitioners.IUCN,
Gland,Switzerland/Cambridge,UK,51pp.
Foster,M.,Amado-Filho,G.M.,Kamenos,N.A.,etal.,2013.
RhodolithsandRhodolithsBeds.ContributionofSCUBA
DivingtoResearchandDiscoveryinMarineEnvironments,
vol.39.,39thed.SmithsonianInstitutionScholarlyPress,
Fukuda,M.V.,Nogueira,J.M.M.,2012.Onanewspeciesof
Nuchalosyllis(Polychaeta:Syllidae),araresyllidgenusonly
knownfromBrazilianwaters.J.Mar.Biol.Assoc.U.K.93(4),
963–966.
Gherardi,D.F.M.,2004.Communitystructureandcarbonate
productionofatemperaterhodolithbankfromArvoredo
Island,SouthernBrazil.Braz.J.Oceanogr.52,207–224.
Kenchington,R.,Hutchings,P.,2012.Science,biodiversityand
Australianmanagementofmarineecosystems.OceanCoast.
Manage.69,194–199.
Moura,R.L.,Secchin,N.A.,Amado-Filho,G.M.,etal.,2013.Spatial
patternsofbenthicmegahabitatsandconservationplanning
intheAbrolhosBank.Cont.ShelfRes.70,109–117.
Pascelli,C.,Riul,P.,Riosmena-Rodríguez,R.,etal.,2013.Seasonal
anddepth-drivenchangesinrhodolithbedstructureand
associatedmacroalgaeoffArvoredoisland(Southeastern
Brazil).Aquat.Bot.111,62–65.
Patin,S.,1999.TheEnvironmentalImpactoftheOffshoreOiland
GasIndustry.EcoMonitorPublishing,EastNorthport,NY,EUA.
Pereira-Filho,G.H.,Amado-Filho,G.M.,Moura,R.L.,etal.,2012.
ExtensiverhodolithbedscoverthesummitsofSouthwestern
AtlanticOceanseamounts.J.Coast.Res.279,261–269.
Reynier,M.,Tâmega,F.T.,Daflon,S.D.,etal.,2015.Long-and
short-termeffectsofsmotheringandburialbydrillcuttings
oncalcareousalgaeinastatic-renewaltest.Environ.Toxicol.
Chem.9999,1–6.
Riul,P.,Lacouth,P.,Pagliosa,P.R.,etal.,2009.Rhodolithbedsat
theeasternmostextremeofSouthAmerica:community
structureofanendangeredenvironment.Aquat.Bot.90,
315–320.
Rullier,F.,Amoureux,L.,1979.CampagnedelaCalypsoaularge
descôtesAtlantiquesdel’AmériqueduSud(1961–1962).I.33.
AnnélidesPolychetes.Annalesdel’InstitutOceanographique
55,145–206.
Santos,A.S.,Riul,P.,Brasil,A.C.S.,etal.,2011.Encrusting
Sabellariidae(Annelida:Polychaeta)inrhodolithbeds,with
descriptionofanewspeciesofSabellariafromBraziliancoast.
J.Mar.Biol.Assoc.U.K.91,425–438(Specialissue).
Simon,T.,Pinheiro,H.T.,Moura,R.L.,etal.,2016.Mesophotic
fishesoftheAbrolhosShelf,thelargestreefecosysteminthe
SouthAtlantic.J.FishBiol.,http://dx.doi.org/10.1111/jfb.12967.
Tâmega,F.T.S.,Spotorno-Oliveira,P.,Figueiredo,M.A.O.,2013.
CatalogueoftheBenthicMarineLifeFromPeregrinoOilField,
CamposBasin,Brazil.InstitutoBiodiversidadeMarinha,Rio
deJaneiro,pp.140.
Tâmega,F.T.S.,Bassi,D.,Figueiredo,M.A.O.,etal.,2014.
Deep-waterrhodolithbedfromcentralBraziliancontinental
shelf,CamposBasin:Corallinealgalandfaunaltaxonomic
composition.J.CoralReefStud.16,21–31.
Testa,V.,Bosence,D.W.,1999.Physicalandbiologicalcontrolson
theformationofcarbonateandsiliciclasticbedformsonthe
North-eastBrazilianshelf.Sedimentology46,279–301.
Villas-Boas,A.B.,Riosmena-Rodriguez,R.,Oliveira-Figueiredo,
M.A.,2013.Communitystructureofrhodolith-formingbeds
onthecentralBraziliancontinentalshelf.HelgolandMar.Res.