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J Appl Ecol. 2019;56:2467–2471. wileyonlinelibrary.com/journal/jpe
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© 2019 The Authors. Journal of Applied Ecology
© 2019 British Ecological Society
Received:17April2019
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Accepted:28July2019
DOI:10.1111/1365-2664.13487
COMMENTARY
The differences between rewilding and restoring an
ecologically degraded landscape
Johan T. du Toit1 | Nathalie Pettorelli2
1DepartmentofWildlandResources,Ut ah
StateUniversit y,Logan,UT,USA
2InstituteofZoology,ZoologicalSocietyof
London,London,UK
Correspondence
JohanT.duToit
Email:johan.dutoit@usu.edu
Funding information
ZoologicalSocietyofLondon
HandlingEditor:MarcCadotte
Abstract
1. Rewilding is adevelopingconcept inecosystemstewardship thatinvolves reor-
ganizing and regenerating wildnessin anecologically degradedlandscape, with
presentandfutureecosystemfunctionbeingofhigherconsiderationthanhistori-
calbenchmarkconditions.Thisapproachdiffersfromecosystemrestorationbut
thetwoconceptsareoftenconflatedbecause(a)they bothrelyonsimilarman-
agementactions(atleastinitially)and(b)itcanbeerroneouslyassumedthatthey
bothaimforsimilarstatesofwildness.
2. Rewilding and r estoring both influe nce biodiversity, and comm on management
actions such asspecies reintroductions (e.g.beaversor wolves) canbe integral
toarewildingproject.However,incontrastwithrestoration,rewildinghaslower
fidelitytotaxonomicprecedentandpromotestaxonomicsubstitutionsforextinct
nativespeciesthatonceunderpinnedthedeliveryofkeyecologicalfunctions.
3. Wesuggesttheadaptivecycleastheappropriateconceptualframeworkinwhich
to distinguish rewilding from ecosystem restoration. The focus of restoration
ecologyistoreturnanecosystemtoasclosetoitsformerstateasispossibleafter
a major distu rbance, by directl y reinstating it on t he ‘foreloop’ of the ad aptive
cycle.Incontrast,rewildingdraws fromthe‘backloop’bypromoting reorganiza-
tionandredevelopmentoftheecosystemunder changingenvironmentalcondi-
tions.Ifenvironmentalconditionshavechangedsosignificantlythataregimeshift
isinevitable,thenrewildingcanfacilitatethedevelopmentofanovelecosystem
tosustaintheprovisionofecosystemservices.
4. Synthesis and applications.Rewildingand restoringboth have theirplacesinbio-
diversityconservation.Ineachcase,theirrespectivemeritsshouldbeweighedin
relationtostakeholderpriorities, prevailingand predictedenvironmentalcondi-
tions,thelevel ofbiologicalorganizationtargetedformanagement,andexisting
and future managementc apacity. Weprovide simple schematic decision-path-
waystoassistinexploringwhetheranecologicallydegradedlandscapemightbea
candidateforrestoration,activerewilding,orpassiverewilding.
KEY WORDS
adaptivecycle,biodiversityconservation,ecologicalrestoration,ecosystemfunction,
functionaltraits,globalchange,novelecosystems,taxonomicsubstitution
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du TOIT and PE TTOR ELLI
1 | REWILDING VS RESTORATION: A
CLASH OF PHILOSOPHY
Rewilding is a rapidly developing conceptinecosystem steward-
ship,highlightedbymanyasapotentiallytransformativeapproach
toconservingand promoting biodiversity.The concept has now
enteredthemainstreamofecology(Perinoetal.,2019;Pettorelli,
Durant,&duToit,2019)anditsmultipledefinitions(reviewedby
Pettorellietal.,2018)havebeendistilleddowntotheir common
essence,whichispromotingtheself-reorganizationorregenera-
tionof wildnessinan ecologicallydegradedlandscapewithmini-
malongoing intervention.That definitionis notsimple, however,
becausewildnesssitselfisanabstractconceptrepresentinganin-
tangiblyuntamedqualityproducedinnature.Furthermore,rewil-
dingisoftenconflatedwithrestoring,becausebothmightinvolve
similar managementac tions(such as translocations) and people
canmistakenlyassumethatbothapproachesaimtoreinstatesim-
ilar types of wildness.In addition, the mediaattention drawnto
Pleistocenerewilding(Donlanetal.,2006) branded rewilding as
therestorationofPleistocenemegafauna,whichwasacaptivating
notionwhileitlasted,despiteitsimpracticalityonanecologically
meaningfulscale(duToit,2019).
Thereisperhapslittleharminthepopularmediareferringtore-
wilding as the processof bringing some wildness back to an area,
whetherrural or urban, in a waythat conflatesrewilding with res-
toration.Nevertheless,assumingnoconceptualdifferencebetween
rewildin g and restoration i s erroneous bec ause each aspires t o a
different state of nature. Restoring implies returning something
to its former condition or state, as with arevered cathedral, clas-
siccarordesiredlandscape. That requires reaching agreement on
what the former state actually was, achieving it through precise
restorationwork,andthencontinuallymaintainingtheagreedstate
despite ch anging environmental cond itions. In contras t, rewilding
meansreturningwildness,whichisuntamed,imperfect,unrulyand
alwayschanginginwaysthatarenotentirelypredictable.Likeit or
not,ecosystemscontinuallyself-organizeandmaintainresilienceby
adaptingtovariable environmental conditions through changes in
their com position, st ructure or f unctioni ng (Holling, 1973; Hollin g
&Gunderson, 2002).Rewildingis thusconceptuallydifferent from
restori ng (Table 1). It is an adaptive a pproach to conser ving eco-
logical functionalit y under changing environmental conditions, to
which historical benchmarks areless relevant than to restoring. It
inherentlyacknowledgesandpromotesunpredictability,whileplac-
ing the emp hasis on funct ion over species com position. It use s a
varietyofmanagementactionsthatcanincludetaxonomicsubstitu-
tions,meaningintroductionsofproxiesforextinctspecies(Bakker&
Svenning,2018),andsofidelitytotaxonomicprecedentismoreflex-
ible thanwith restoring. In principle, taxonomic substitution could
prioritizefunctionallyappropriateexoticspeciesfacingconservation
threat s in their nati ve ranges, alt hough in prac tice less con trover-
sial optio ns—such as various l ivestock bre eds—are more commo n.
Rewilding canalsobeappliedinurban and ruralareas, beinginclu-
siveoftheagencyofpeopleinnature.
Rewilding can operate at multiple levelsfrom genestoecosys-
tems, andmanagerscan achieve rewilding in several wayssuch as
facilitatinggeneflow,translocatingpropagulesorwholeorganisms,
conductingcivil engineeringorcombinationsthereof.For example
genetic rescue (Whiteley, Fitzpatrick, Funk, & Tallmon, 2015) in-
volvesfacilitatinggeneflowintoapopulationfacingextinctiondue
to inbreeding depression, which might be called restoration (e.g.
Johnsonetal.,2010)butisactuallyrewildingatthemolecularlevel.
Therecipientgenepoolbecomesreorganizedwithanewdiversityof
allelesincludingsomethatwerenevertherebefore,afterwhichthe
successorfailureoftheexerciseisoutofthemanagers’hands.Itde-
pendsonthegeneticanddem ographicviabilityofthe‘rescued’pop-
ulation under changing environmentalconditions (Hedrick, Adams,
&Vucetich,2011).Atthe otherextreme,theOostvaardersplassen
inthe Netherlandsisan example of rewilding arisingfrom a major
civilengineeringproject.Itinvolveddykes,poldersandpumpstoex-
poseanareaofformerseabedforcolonizationbyterrestrialspecies,
among whi ch some were intro duced and some c ontinue to arri ve
unassisted(Marris,2009).Inallcases,thesystemiscontinuallyself-
organizingastheenvironmentchanges,andthefunctionalcomposi-
tionofthesystemisahigherconsiderationthanthetaxonomyofits
operatingcomponents(e.g.Garridoetal.,2019).
2 | THE POWER OF METAPHORS
The effective communic ation of science, especially to non-scien-
tists , depends on the u se of metaphors (O lson, Arroyo-Santo s, &
Vergara-Silv a, 2019).T hese are verbal a nd graphical m odels used
TABLE 1 Acomparisonofrestoringandrewildingatthe
landscapescale,expressedinrelationtoasetofdistinguishing
attributes
Distinguishing
attributes Restoring Rewilding
Relevanceofhistorical
benchmarks
Higher Lower
Fidelit ytotaxonomic
precedent
Higher Lower
Predictabilityofsys-
temdynamics
Higher Lower
Management
commitment
Continuous Tap e red
Motivationfor
translocations
Species
composition
Functionaltype
composition
Taxonomic
substitutions
Resisted Accepted
Environmentally
drivensystem
transformation
Resisted Accepted
Emergenceofnovel
ecosystems
Resisted Accepted
Peopleandnature Moreexclusive Moreinclusive
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du TOIT and PE TTOR ELLI
ascognitivetools toassistin expressing,understanding, exploring
and develo ping complex co ncepts. The y do have their limit ations,
however,andsoshouldbeusedasaidsandneverinterpretedastrue
and full re presentat ions. Here we of fer two met aphors to hel p in
differentiating between restoring and rewilding,with full recogni-
tionthatneithercanrepresentallthecomplexitiesanddynamicsof
ecosystems.
2.1 | The adaptive cycle as a distinguishing
conceptual framework
Theadaptivecycle (Holling &Gunderson,2002), whichisawidely
successfulmetaphorforthedynamicsofsocial–ecologicalsystems
(Walker,Holling, Carpenter,& Kinzig,2004), has become avalued
heuristic toolin ecosystemstewardship (Chapin, Kofinas,& Folke,
2009).Here,weproposetheadaptivecycleastheappropriatecon-
ceptualframeworkinwhichtoidentifythefundamentaldifferences
betweenrewildingandrestoringanecologicallydegradedlandscape
(Figure1).
Followingamajordisturbance,anecosystemgenerallyrecovers
withspeciesreassemblingandbiomassgrowing (rphase).Available
resourcesbecomeexploited,withsuccessionleadingtoanincreas-
ingly connected system withmountingpotentialforniche occupa-
tion.Thisleadstotheaccumulationandconservationofresourcesin
aclimaxstate(Kphase),withthetransitionfromexploitationtocon-
servation(r‐K )beingreferredtoasthe‘foreloop’ofthecycle.Then
withthenextfire,hurricane,drought,outbreakorover-harvest,the
potential andconnectednessarerapidlyreleased(Ωphase) andan
unpredictable‘backloop’leadstoaphaseofreorganization(αphas e).
Depending on the response diversityconser ved within each func-
tionalgroup(Awiti,2011;Elmqvistetal.,2003),thefreedresources
thenallowtheecosystemtoredevelopbycyclingintoanewrphase
asgovernedbyprevailingconditions.
Restorationisconcernedwithshortcuttingthebackloopandfast
trackingtheforelooptomovethesystemfromΩdirectlybacktoK
as quickly and predictably as possible after adisturbance. In con-
trast,rewildingdrawsfromthebackloop,facilitatingreorganization
andthetransitionfromαtorphasessothatthesystemcanmaintain
resiliencebyadaptingtochangedconditions,obviatingtheneedfor
continuousmanagement.However,iftheenvironmentalconditions
havechanged so significantlythataregime shiftisinevitable, then
alternative rewilding approaches could be considered. Managers
could eith er take a ‘wait-and-see’ ap proach (passive rew ilding) as
anovel ecosystem develops on its own, or intervene initially with
species i ntroductions a nd/or engine ering works (acti ve rewilding)
to generate a n ovel ecosystem tha t might (hopefully) su stain the
provision of ecosystem services under projected environmental
conditions.
2.2 | Classic car or enduring transport system?
Metaphorsareespeciallyhelpfulinunderstandingabstractconcepts
byreferencetophysicalentities,an dweventuretowieldthatcogni-
tivetooltodistinguishbetweenrestoringandrewildingbyreference
tooldmotorcars.Thisofcourserequiresthereadertooverlookthe
obvious inability ofcars todisplay the adaptive, self-organizing be-
haviourofecosystems.
Adistinctivefeatureofpresent-dayCubaisanabundanceofcars
ofmid-20th century vintage that are still in ser vice. From its pro-
ductiondate, eachcar would have been subjected to multipledis-
turbances that its owners (‘managers’)could haveresponded toin
variouswaysdependingontheircircumstances.Whenoneormore
essentialpartsfailedandiforiginalreplacementpartswereunavail-
ableorunaffordable,andiftherewasnoconsiderationorpossibility
ofusingnon-originalparts,thenthecarwouldhavebecomederelict.
Restoringwouldbepossibleiforiginalpartscouldbeprocuredandif
therequisiteresourcesandexpertisecouldbeinvestedintheproj-
ect. A lternativel y,th e necessit y of maintainin g function ality could
drivetheownerstousesomenon-originalpartsandpossiblyadapt
bothvehicleandpartsintheprocess.Thiswouldallowavaluedser-
vicetobe maintained inanenvironmentwithaltered options,asin
present-day Cuba.There,whatmight now appear tobe astill-run-
ning classic Americancar could actuallybe powered by an engine
fromaRussiancement mixerwithelectrical wiringstrippedfroma
Chinese washingmachine.Inthiscase,restoringis notanoptionin
anenvironment ofdisturbanceandchange,soapragmaticsolution
hasemerged.Inconcept,thatsolutionistoatransportsystemwhat
rewildingistoanecosystem.
3 | MOVING FORWARD
Restoringandrewildingmaybeconsideredsimilaronlytotheextent
that they b oth involve biodive rsity and com ponents of one co uld
be neste d within the other. For exa mple restoring at t he species
level(e.g.beaversCas torspp.,or wolvesCanis lupus)mightbeinte-
gral to rewilding at theecosystem level(Figure2),but rewilding is
never part of restoration. Istherevalue in distinguishing between
theseconceptsanddoesrewildingstandaloneasaviablesteward-
ship option? We argue ‘yes’ because for any landscape, whether
FIGURE 1 TheadaptivecycleofHollingandGunderson(2002)
witharrowsaddedforthestewardshipoptionsofrewildingand
restoring,whichoperateatdifferentstageswithinthisconceptual
framework
R
e
w
i
l
d
i
n
g
R
e
o
r
g
a
n
i
z
a
t
i
o
n
C
o
n
s
e
r
v
a
t
i
o
n
E
x
p
l
o
i
t
a
t
i
o
n
R
e
w
i
l
d
i
n
g
R
e
l
e
a
s
e
R
e
s
t
o
r
i
n
g
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Journal of Applied Ecology
du TOIT and PE TTOR ELLI
ecologicallydegradedornot,itisdifficulttoimaginehowconserving
biodiversity andecosystemservicescould be possibleinpredicted
future scenarios without rewilding. Simply stated, anthropogenic
environmental forcing makes ecosystem restoration a diminishing
option. That is why restoration ecologists now find themselves at
acrossroads(Hobbs,2018)wherenewconceptslikenovelandde-
signed ecosystems (Higgs, 2017) are causingbearings to be ques-
tioned.Somesuggestextendingthe‘bigtent’ofrestorationecology
to include these concepts (Miller & Bestelmeyer, 2016) whereas
otherssuggestrenamingrestoration(Rohwer&Marris,2016).Now,
themisunderstandingofrewilding and itsconflation with restoring
havecaused yet otherstogosofarastocall for banningthe term
rewilding(‘abuzz-word’)fromscientific,policyandconser vationdis-
course(Haywoodetal.,2019).Nevertheless,rewildingandrestoring
standasdistinctconcepts,eachwithitsownlogicalplacewithinthe
frameworkofthea daptivec ycle(F ig ure1).Fur therm ore,thed is tinc-
tions between the concepts (Table1)canassistinoperationalizing
thedecision-makingprocesswhena group ofstakeholdersbegins
discussingacourseofactionforanecologicallydegradedlandscape
(Figure 2). In practice,thedecisionpathwaysaremore likelytofa-
cilitate theprocess by whichstakeholdersmuddle through to con-
sensusthantoprovideaquicklyadoptableroadmaptowardsafixed
objective.Debatingprioritiesandexploringtheirimplicationsforces
stakeholderstoconfrontenvironmentalchanges,considerhowre-
versible(ornot)theyare,evaluatethecostsoffuturecommitments,
andformrealisticexpectations.
4 | CONCLUSIONS
Rewilding i s a concept that em braces new op portuni ties and pro-
videsawayforwardforecologicallydegradedlandscapeswhenres-
torationisnotanoption.Aswithrethinkinganargument,retooling
afactory, or reorganizing an institution, rewilding alandscape isa
progressiveresponse totheneedforenhanced functionalityunder
changed conditions. Rewilding and restoring are thus different
conceptsandeach has itsplace in ecosystem stewardship. In each
case, the respectivemeritsshouldbeweighedinrelation to stake-
holderpriorities,prevailingandpredictedenvironmentalconditions,
thelevelofbiological organization targeted for management,and
existingandfuturemanagementcapacity(Figure2).Becauserewil-
ding focuses on processes and functions, the approach challenges
conservationscientistsandmanagerstoconsiderwhy a functional
type is i mportant b efore worryin g about which species sh ould or
shouldno tb ep resen t.Thist ypeofth inkingisals od evelopinginthe-
oreticalecology,withagrowingnumberof studieshighlightingthe
importanceoffunctionaltraitdistributionforecosystemprocesses
and ser vices (Duncan, T hompson, & Petto relli, 2015). Such ideas
are discon certing to th ose who argue t hat rewilding sh ould focus
exclusivelyonbiodiversityandconsiderecosystemservicesonlyas
co-benefits(Genes,Svenning,Pires,&Fernandez,2019).Wildeco-
systemsare,however,asdiverseastheirenvironmentalconstraints
allow,whileproces sesandfunctionsarepartofbiod iversit ya ny way.
Therefore any rewilding project, whether initiated for e cosystem
servicesornot,willultimatelypromotelocalbiodiversity.Indeed,the
riseoftherewildingconceptisasignthatpragmaticnewapproaches
are urgently needed to conserve both biodiversity and ecosystem
servicesunderrapidlychangingenvironmentalconditions.
ACKNOWLEDGEMENTS
Theideasinthispaperbenefitedfromdiscussionsamongpresenters
atapublicscienceevent entitled ‘Rewildingin a changing climate'
organizedbytheZoologicalSocietyofLondonatTheRegent'sPark,
Lond on, inDec emb er2018.WethankMa rcCadottean dt woa nony-
mousreviewersfortheirhelpfulcommentsonearlierdrafts,andto
BrianKartchnerforhelpwithgraphics.
CONFLICT OF INTEREST
Theauthorshavenoconflictsofinterestwiththepublicationofthis
article.
FIGURE 2 Decisionpathwaysinvolved
inexploringwhetheranecologically
degradedlandscapemightbeacandidate
forrestoration,activerewildingorpassive
rewilding
Stakeholder
priority?
Undefined
wildness
Can key
nave species be
restored?
Yes
No Taxonomic
substuon?
Impossible
Management
commitment?
Connuous
Tapered
Restoraon
Acve
rewilding
Passive
rewilding
Possible
Ecologically
degraded
landscape
Historical
community
structure
Ecosystem
funcon
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du TOIT and PE TTOR ELLI
AUTHORS' CONTRIBUTIONS
J.T.d.T.andN.P.conceivedtheideas,wrotethepaperandgavefinal
approvalforpublication.
DATA AVA ILAB ILITY STATE MEN T
Therearenodatainvolvedinthispaperandsononearearchived.
ORCID
Johan T. Toit https://orcid.org/0000-0003-0705-7117
Nathalie Pettorelli https://orcid.org/0000-0002-1594-6208
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How to cite this article:duToitJT,PettorelliN.Thedifferences
betweenrewildingandrestoringanecologicallydegraded
landscape.J Appl Ecol. 2019;56:2467–2471. h t t p s : / / d o i .
org /10.1111/1365-2664.13487