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The differences between rewilding and restoring an ecologically degraded landscape

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Journal of Applied Ecology
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Abstract and Figures

Rewilding is a developing concept in ecosystem stewardship that involves reorganizing and regenerating wildness in an ecologically degraded landscape, with present and future ecosystem function being of higher consideration than historical benchmark conditions. This approach differs from ecosystem restoration but the two concepts are often conflated because (a) they both rely on similar management actions (at least initially) and (b) it can be erroneously assumed that they both aim for similar states of wildness. Rewilding and restoring both influence biodiversity, and common management actions such as species reintroductions (e.g. beavers or wolves) can be integral to a rewilding project. However, in contrast with restoration, rewilding has lower fidelity to taxonomic precedent and promotes taxonomic substitutions for extinct native species that once underpinned the delivery of key ecological functions. We suggest the adaptive cycle as the appropriate conceptual framework in which to distinguish rewilding from ecosystem restoration. The focus of restoration ecology is to return an ecosystem to as close to its former state as is possible after a major disturbance, by directly reinstating it on the ‘foreloop’ of the adaptive cycle. In contrast, rewilding draws from the ‘backloop’ by promoting reorganization and redevelopment of the ecosystem under changing environmental conditions. If environmental conditions have changed so significantly that a regime shift is inevitable, then rewilding can facilitate the development of a novel ecosystem to sustain the provision of ecosystem services. Synthesis and applications. Rewilding and restoring both have their places in biodiversity conservation. In each case, their respective merits should be weighed in relation to stakeholder priorities, prevailing and predicted environmental conditions, the level of biological organization targeted for management, and existing and future management capacity. We provide simple schematic decision‐pathways to assist in exploring whether an ecologically degraded landscape might be a candidate for restoration, active rewilding, or passive rewilding.
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J Appl Ecol. 2019;56:2467–2471. wileyonlinelibrary.com/journal/jpe  
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 2467
© 2019 The Authors. Journal of Applied Ecology
© 2019 British Ecological Society
Received:17April2019 
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Accepted:28July2019
DOI:10.1111/1365-2664.13487
COMMENTARY
The differences between rewilding and restoring an
ecologically degraded landscape
Johan T. du Toit1| Nathalie Pettorelli2
1DepartmentofWildlandResources,Ut ah
StateUniversit y,Logan,UT,USA
2InstituteofZoology,ZoologicalSocietyof
London,London,UK
Correspondence
JohanT.duToit
Email:johan.dutoit@usu.edu
Funding information
ZoologicalSocietyofLondon
HandlingEditor:MarcCadotte
Abstract
1. Rewilding is adevelopingconcept inecosystemstewardship thatinvolves reor-
ganizing and regenerating wildnessin anecologically degradedlandscape, with
presentandfutureecosystemfunctionbeingofhigherconsiderationthanhistori-
calbenchmarkconditions.Thisapproachdiffersfromecosystemrestorationbut
thetwoconceptsareoftenconflatedbecause(a)they bothrelyonsimilarman-
agementactions(atleastinitially)and(b)itcanbeerroneouslyassumedthatthey
bothaimforsimilarstatesofwildness.
2. Rewilding and r estoring both influe nce biodiversity, and comm on management
actions such asspecies reintroductions (e.g.beaversor wolves) canbe integral
toarewildingproject.However,incontrastwithrestoration,rewildinghaslower
fidelitytotaxonomicprecedentandpromotestaxonomicsubstitutionsforextinct
nativespeciesthatonceunderpinnedthedeliveryofkeyecologicalfunctions.
3. Wesuggesttheadaptivecycleastheappropriateconceptualframeworkinwhich
to distinguish rewilding from ecosystem restoration. The focus of restoration
ecologyistoreturnanecosystemtoasclosetoitsformerstateasispossibleafter
a major distu rbance, by directl y reinstating it on t he ‘foreloop’ of the ad aptive
cycle.Incontrast,rewildingdraws fromthe‘backloop’bypromoting reorganiza-
tionandredevelopmentoftheecosystemunder changingenvironmentalcondi-
tions.Ifenvironmentalconditionshavechangedsosignificantlythataregimeshift
isinevitable,thenrewildingcanfacilitatethedevelopmentofanovelecosystem
tosustaintheprovisionofecosystemservices.
4. Synthesis and applications.Rewildingand restoringboth have theirplacesinbio-
diversityconservation.Ineachcase,theirrespectivemeritsshouldbeweighedin
relationtostakeholderpriorities, prevailingand predictedenvironmentalcondi-
tions,thelevel ofbiologicalorganizationtargetedformanagement,andexisting
and future managementc apacity. Weprovide simple schematic decision-path-
waystoassistinexploringwhetheranecologicallydegradedlandscapemightbea
candidateforrestoration,activerewilding,orpassiverewilding.
KEY WORDS
adaptivecycle,biodiversityconservation,ecologicalrestoration,ecosystemfunction,
functionaltraits,globalchange,novelecosystems,taxonomicsubstitution
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1 | REWILDING VS RESTORATION: A
CLASH OF PHILOSOPHY
Rewilding is a rapidly developing conceptinecosystem steward-
ship,highlightedbymanyasapotentiallytransformativeapproach
toconservingand promoting biodiversity.The concept has now
enteredthemainstreamofecology(Perinoetal.,2019;Pettorelli,
Durant,&duToit,2019)anditsmultipledefinitions(reviewedby
Pettorellietal.,2018)havebeendistilleddowntotheir common
essence,whichispromotingtheself-reorganizationorregenera-
tionof wildnessinan ecologicallydegradedlandscapewithmini-
malongoing intervention.That definitionis notsimple, however,
becausewildnesssitselfisanabstractconceptrepresentinganin-
tangiblyuntamedqualityproducedinnature.Furthermore,rewil-
dingisoftenconflatedwithrestoring,becausebothmightinvolve
similar managementac tions(such as translocations) and people
canmistakenlyassumethatbothapproachesaimtoreinstatesim-
ilar types of wildness.In addition, the mediaattention drawnto
Pleistocenerewilding(Donlanetal.,2006) branded rewilding as
therestorationofPleistocenemegafauna,whichwasacaptivating
notionwhileitlasted,despiteitsimpracticalityonanecologically
meaningfulscale(duToit,2019).
Thereisperhapslittleharminthepopularmediareferringtore-
wilding as the processof bringing some wildness back to an area,
whetherrural or urban, in a waythat conflatesrewilding with res-
toration.Nevertheless,assumingnoconceptualdifferencebetween
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 arevered cathedral, clas-
siccarordesiredlandscape. That requires reaching agreement on
what the former state actually was, achieving it through precise
restorationwork,andthencontinuallymaintainingtheagreedstate
despite ch anging environmental cond itions. In contras t, rewilding
meansreturningwildness,whichisuntamed,imperfect,unrulyand
alwayschanginginwaysthatarenotentirelypredictable.Likeit or
not,ecosystemscontinuallyself-organizeandmaintainresilienceby
adaptingtovariable environmental conditions through changes in
their com position, st ructure or f unctioni ng (Holling, 1973; Hollin g
&Gunderson, 2002).Rewildingis thusconceptuallydifferent 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 areless relevant than to restoring. It
inherentlyacknowledgesandpromotesunpredictability,whileplac-
ing the emp hasis on funct ion over species com position. It use s a
varietyofmanagementactionsthatcanincludetaxonomicsubstitu-
tions,meaningintroductionsofproxiesforextinctspecies(Bakker&
Svenning,2018),andsofidelitytotaxonomicprecedentismoreflex-
ible thanwith restoring. In principle, taxonomic substitution could
prioritizefunctionallyappropriateexoticspeciesfacingconservation
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 canalsobeappliedinurban and ruralareas, beinginclu-
siveoftheagencyofpeopleinnature.
Rewilding can operate at multiple levelsfrom genestoecosys-
tems, andmanagerscan achieve rewilding in several wayssuch as
facilitatinggeneflow,translocatingpropagulesorwholeorganisms,
conductingcivil engineeringorcombinationsthereof.For example
genetic rescue (Whiteley, Fitzpatrick, Funk, & Tallmon, 2015) in-
volvesfacilitatinggeneflowintoapopulationfacingextinctiondue
to inbreeding depression, which might be called restoration (e.g.
Johnsonetal.,2010)butisactuallyrewildingatthemolecularlevel.
Therecipientgenepoolbecomesreorganizedwithanewdiversityof
allelesincludingsomethatwerenevertherebefore,afterwhichthe
successorfailureoftheexerciseisoutofthemanagers’hands.Itde-
pendsonthegeneticanddem ographicviabilityofthe‘rescued’pop-
ulation under changing environmentalconditions (Hedrick, Adams,
&Vucetich,2011).Atthe otherextreme,theOostvaardersplassen
inthe Netherlandsisan example of rewilding arisingfrom a major
civilengineeringproject.Itinvolveddykes,poldersandpumpstoex-
poseanareaofformerseabedforcolonizationbyterrestrialspecies,
among whi ch some were intro duced and some c ontinue to arri ve
unassisted(Marris,2009).Inallcases,thesystemiscontinuallyself-
organizingastheenvironmentchanges,andthefunctionalcomposi-
tionofthesystemisahigherconsiderationthanthetaxonomyofits
operatingcomponents(e.g.Garridoetal.,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 Acomparisonofrestoringandrewildingatthe
landscapescale,expressedinrelationtoasetofdistinguishing
attributes
Distinguishing
attributes Restoring Rewilding
Relevanceofhistorical
benchmarks
Higher Lower
Fidelit ytotaxonomic
precedent
Higher Lower
Predictabilityofsys-
temdynamics
Higher Lower
Management
commitment
Continuous Tap e red
Motivationfor
translocations
Species
composition
Functionaltype
composition
Taxonomic
substitutions
Resisted Accepted
Environmentally
drivensystem
transformation
Resisted Accepted
Emergenceofnovel
ecosystems
Resisted Accepted
Peopleandnature Moreexclusive Moreinclusive
    
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ascognitivetools toassistin expressing,understanding, exploring
and develo ping complex co ncepts. The y do have their limit ations,
however,andsoshouldbeusedasaidsandneverinterpretedastrue
and full re presentat ions. Here we of fer two met aphors to hel p in
differentiating between restoring and rewilding,with full recogni-
tionthatneithercanrepresentallthecomplexitiesanddynamicsof
ecosystems.
2.1 | The adaptive cycle as a distinguishing
conceptual framework
Theadaptivecycle (Holling &Gunderson,2002), whichisawidely
successfulmetaphorforthedynamicsofsocial–ecologicalsystems
(Walker,Holling, Carpenter,& Kinzig,2004), has become avalued
heuristic toolin ecosystemstewardship (Chapin, Kofinas,& Folke,
2009).Here,weproposetheadaptivecycleastheappropriatecon-
ceptualframeworkinwhichtoidentifythefundamentaldifferences
betweenrewildingandrestoringanecologicallydegradedlandscape
(Figure1).
Followingamajordisturbance,anecosystemgenerallyrecovers
withspeciesreassemblingandbiomassgrowing (rphase).Available
resourcesbecomeexploited,withsuccessionleadingtoanincreas-
ingly connected system withmountingpotentialforniche occupa-
tion.Thisleadstotheaccumulationandconservationofresourcesin
aclimaxstate(Kphase),withthetransitionfromexploitationtocon-
servation(r‐K )beingreferredtoasthe‘foreloop’ofthecycle.Then
withthenextfire,hurricane,drought,outbreakorover-harvest,the
potential andconnectednessarerapidlyreleased(Ωphase) andan
unpredictable‘backloop’leadstoaphaseofreorganization(αphas e).
Depending on the response diversityconser ved within each func-
tionalgroup(Awiti,2011;Elmqvistetal.,2003),thefreedresources
thenallowtheecosystemtoredevelopbycyclingintoanewrphase
asgovernedbyprevailingconditions.
Restorationisconcernedwithshortcuttingthebackloopandfast
trackingtheforelooptomovethesystemfromΩdirectlybacktoK
as quickly and predictably as possible after adisturbance. In con-
trast,rewildingdrawsfromthebackloop,facilitatingreorganization
andthetransitionfromαtorphasessothatthesystemcanmaintain
resiliencebyadaptingtochangedconditions,obviatingtheneedfor
continuousmanagement.However,iftheenvironmentalconditions
havechanged so significantlythataregime shiftisinevitable, then
alternative rewilding approaches could be considered. Managers
could eith er take a ‘wait-and-see’ ap proach (passive rew ilding) as
anovel 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?
Metaphorsareespeciallyhelpfulinunderstandingabstractconcepts
byreferencetophysicalentities,an dweventuretowieldthatcogni-
tivetooltodistinguishbetweenrestoringandrewildingbyreference
tooldmotorcars.Thisofcourserequiresthereadertooverlookthe
obvious inability ofcars todisplay the adaptive, self-organizing be-
haviourofecosystems.
Adistinctivefeatureofpresent-dayCubaisanabundanceofcars
ofmid-20th century vintage that are still in ser vice. From its pro-
ductiondate, eachcar would have been subjected to multipledis-
turbances that its owners (‘managers’)could haveresponded toin
variouswaysdependingontheircircumstances.Whenoneormore
essentialpartsfailedandiforiginalreplacementpartswereunavail-
ableorunaffordable,andiftherewasnoconsiderationorpossibility
ofusingnon-originalparts,thenthecarwouldhavebecomederelict.
Restoringwouldbepossibleiforiginalpartscouldbeprocuredandif
therequisiteresourcesandexpertisecouldbeinvestedintheproj-
ect. A lternativel y,th e necessit y of maintainin g function ality could
drivetheownerstousesomenon-originalpartsandpossiblyadapt
bothvehicleandpartsintheprocess.Thiswouldallowavaluedser-
vicetobe maintained inanenvironmentwithaltered options,asin
present-day Cuba.There,whatmight now appear tobe astill-run-
ning classic Americancar could actuallybe powered by an engine
fromaRussiancement mixerwithelectrical wiringstrippedfroma
Chinese washingmachine.Inthiscase,restoringis notanoptionin
anenvironment ofdisturbanceandchange,soapragmaticsolution
hasemerged.Inconcept,thatsolutionistoatransportsystemwhat
rewildingistoanecosystem.
3 | MOVING FORWARD
Restoringandrewildingmaybeconsideredsimilaronlytotheextent
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.beaversCas torspp.,or wolvesCanis lupus)mightbeinte-
gral to rewilding at theecosystem level(Figure2),but rewilding is
never part of restoration. Istherevalue in distinguishing between
theseconceptsanddoesrewildingstandaloneasaviablesteward-
ship option? We argue ‘yes’ because for any landscape, whether
FIGURE 1 TheadaptivecycleofHollingandGunderson(2002)
witharrowsaddedforthestewardshipoptionsofrewildingand
restoring,whichoperateatdifferentstageswithinthisconceptual
framework
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2470 
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du TOIT and PE TTOR ELLI
ecologicallydegradedornot,itisdifficulttoimaginehowconserving
biodiversity andecosystemservicescould be possibleinpredicted
future scenarios without rewilding. Simply stated, anthropogenic
environmental forcing makes ecosystem restoration a diminishing
option. That is why restoration ecologists now find themselves at
acrossroads(Hobbs,2018)wherenewconceptslikenovelandde-
signed ecosystems (Higgs, 2017) are causingbearings to be ques-
tioned.Somesuggestextendingthe‘bigtent’ofrestorationecology
to include these concepts (Miller & Bestelmeyer, 2016) whereas
otherssuggestrenamingrestoration(Rohwer&Marris,2016).Now,
themisunderstandingofrewilding and itsconflation with restoring
havecaused yet otherstogosofarastocall for banningthe term
rewilding(‘abuzz-word’)fromscientific,policyandconser vationdis-
course(Haywoodetal.,2019).Nevertheless,rewildingandrestoring
standasdistinctconcepts,eachwithitsownlogicalplacewithinthe
frameworkofthea daptivec ycle(F ig ure1).Fur therm ore,thed is tinc-
tions between the concepts (Table1)canassistinoperationalizing
thedecision-makingprocesswhena group ofstakeholdersbegins
discussingacourseofactionforanecologicallydegradedlandscape
(Figure 2). In practice,thedecisionpathwaysaremore likelytofa-
cilitate theprocess by whichstakeholdersmuddle through to con-
sensusthantoprovideaquicklyadoptableroadmaptowardsafixed
objective.Debatingprioritiesandexploringtheirimplicationsforces
stakeholderstoconfrontenvironmentalchanges,considerhowre-
versible(ornot)theyare,evaluatethecostsoffuturecommitments,
andformrealisticexpectations.
4 | CONCLUSIONS
Rewilding i s a concept that em braces new op portuni ties and pro-
videsawayforwardforecologicallydegradedlandscapeswhenres-
torationisnotanoption.Aswithrethinkinganargument,retooling
afactory, or reorganizing an institution, rewilding alandscape isa
progressiveresponse totheneedforenhanced functionalityunder
changed conditions. Rewilding and restoring are thus different
conceptsandeach has itsplace in ecosystem stewardship. In each
case, the respectivemeritsshouldbeweighedinrelation to stake-
holderpriorities,prevailingandpredictedenvironmentalconditions,
thelevelofbiological organization targeted for management,and
existingandfuturemanagementcapacity(Figure2).Becauserewil-
ding focuses on processes and functions, the approach challenges
conservationscientistsandmanagerstoconsiderwhy a functional
type is i mportant b efore worryin g about which species sh ould or
shouldno tb ep resen t.Thist ypeofth inkingisals od evelopinginthe-
oreticalecology,withagrowingnumberof studieshighlightingthe
importanceoffunctionaltraitdistributionforecosystemprocesses
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
exclusivelyonbiodiversityandconsiderecosystemservicesonlyas
co-benefits(Genes,Svenning,Pires,&Fernandez,2019).Wildeco-
systemsare,however,asdiverseastheirenvironmentalconstraints
allow,whileproces sesandfunctionsarepartofbiod iversit ya ny way.
Therefore any rewilding project, whether initiated for e cosystem
servicesornot,willultimatelypromotelocalbiodiversity.Indeed,the
riseoftherewildingconceptisasignthatpragmaticnewapproaches
are urgently needed to conserve both biodiversity and ecosystem
servicesunderrapidlychangingenvironmentalconditions.
ACKNOWLEDGEMENTS
Theideasinthispaperbenefitedfromdiscussionsamongpresenters
atapublicscienceevent entitled Rewildingin a changing climate'
organizedbytheZoologicalSocietyofLondonatTheRegent'sPark,
Lond on, inDec emb er2018.WethankMa rcCadottean dt woa nony-
mousreviewersfortheirhelpfulcommentsonearlierdrafts,andto
BrianKartchnerforhelpwithgraphics.
CONFLICT OF INTEREST
Theauthorshavenoconflictsofinterestwiththepublicationofthis
article.
FIGURE 2 Decisionpathwaysinvolved
inexploringwhetheranecologically
degradedlandscapemightbeacandidate
forrestoration,activerewildingorpassive
rewilding
Stakeholder
priority?
Undefined
wildness
Can key
nave species be
restored?
Yes
No Taxonomic
substuon?
Impossible
Management
commitment?
Connuous
Tapered
Restoraon
Acve
rewilding
Passive
rewilding
Possible
Ecologically
degraded
landscape
Historical
community
structure
Ecosystem
funcon
    
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 2471
Journal of Applied Ecology
du TOIT and PE TTOR ELLI
AUTHORS' CONTRIBUTIONS
J.T.d.T.andN.P.conceivedtheideas,wrotethepaperandgavefinal
approvalforpublication.
DATA AVA ILAB ILITY STATE MEN T
Therearenodatainvolvedinthispaperandsononearearchived.
ORCID
Johan T. Toit https://orcid.org/0000-0003-0705-7117
Nathalie Pettorelli https://orcid.org/0000-0002-1594-6208
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... Here, considerable potential for ecosystem restoration and rewilding exists [22]. Currently, 'passive rewilding' [93], i.e. the absence of human restoration interventions, prevails on abandoned land. We have shown here that the continued lack of grazing and the associated intensification of fire regimes has likely had negative ecosystem consequences. ...
... We have shown here that the continued lack of grazing and the associated intensification of fire regimes has likely had negative ecosystem consequences. It might, therefore, be more desirable to follow two potential pathways to rewilding: (i) a reintroduction of large herbivores to their native range with management tapering out over time ('active rewilding' sensu [93], (ii) an expansion of traditional livestock grazing systems into abandoned pasture areas that mirror grazing intensity and patterns of native grazers (partial restoration). ...
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Shifts in fire regimes can trigger rapid changes in ecosystem functioning and biodiversity. We synthesize evidence for patterns, causes and consequences of recent change in fire regimes across the Eurasian steppes, a neglected global fire hotspot. Political and economic turmoil following the break-up of the Soviet Union in 1991 triggered abrupt land abandonment over millions of hectares and a collapse of livestock populations. The build-up of vegetation as fuel, rural depopulation and deteriorating fire control led to a rapid increase in fire size, area burned and fire frequency. Fire regimes were also driven by drought, but likely only after fuel had accumulated. Increased fire disturbance resulted in grass encroachment, vegetation homogenization and decreasing plant species diversity. Feedback loops due to the high grass flammability were likely. Direct and carry-on effects on birds, keystone small mammals and insects were largely negative. Nutrient cycling and carbon balance changed, but these changes have yet to be quantified. The regime of large and frequent fires persisted until ca 2010 but shifted back to a more grazing-controlled regime as livestock populations recovered, reinforced by increasing precipitation. Key future research topics include the effects of future climate change, changing pyrodiversity and pyric herbivory on ecosystem resilience. Ongoing steppe restoration and rewilding efforts, and integrated fire management will benefit from a better understanding of fire regimes. This article is part of the theme issue ‘Novel fire regimes under climate changes and human influences: impacts, ecosystem responses and feedbacks’.
... The term 'rewilding' was first coined in the 1990s as a response to the decline of biodiversity and trophic (food web) relationships in terrestrial ecosystems, and is now considered a nature-based solution [8][9][10][11] Although rewilding has gained momentum as a conservation discipline, scientific acceptance of a standard definition of it still appears to be lacking 12 . The application of the term rewilding in relation to other conservation practices, such as restoration, and the end point to which an ecosystem should be rewilded, has been debated 13,14 . There are key differences in the philosophies of restoration and rewilding, with rewilding placing less emphasis on past baselines and taxonomic fidelity than restoration, as well as accepting alternative ecological outcomes and greater social participation14. ...
... With environmental changes and shifting baselines comes potentially greater acceptance of novel ecosystems as an outcome 16,17 , as well as proliferation of more adaptable but harder to control weedy species, such as jellyfish 18 . The science and practice of rewilding the sea is less developed than that of terrestrial rewilding, in part due to added complexities of managing activities within the marine environment, accessibility and relative lack of research and monitoring 14,19 . With increasing pressures, terrestrial and marine ecosystems face greater risk of abrupt ecological tipping points, which can present challenges for human uses of natural resources and are more difficult to detect in marine environments where monitoring is lacking 20,21 . ...
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Public concern over global climate change and biodiversity loss has accelerated international efforts to restore natural ecosystems through nature-based solutions. Rewilding is a growing conservation approach encompassing the recovery of ecological and trophic complexity through interventions such as habitat restoration and/or species reintroduction. Here we explore the nascent efforts of marine rewilding using a systems thinking methodology to inform a systematic review and iterative thematic analysis. Marine rewilding involves a diverse range of interventions, showing similarities in ecological principles with terrestrial rewilding, yet it diverges from terrestrial rewilding in the scale of initiatives, predictability of outcomes, and the prominence of social inclusion. To make progress in offering unifying concepts, we propose a definition for marine rewilding: a systemic process requiring deliberate human intervention that involves community participation and ocean stewardship to regenerate degraded marine ecosystems.
... This approach is thought not only to enhance biodiversity but also to contribute to ecosystem resilience and functioning (Perino et al., 2019). Rewilding can improve habitat connectivity and promote the recovery of native species, thereby supporting complex ecological interactions (du Toit & Pettorelli, 2019). The integration of rewilding into land management practices holds promise for ecological restoration and sustainable agriculture, yet there remains a need for empirical evidence to fully understand its benefits and implications. ...
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Organic farms have been shown to harbour larger and more diverse invertebrate populations and associated ecosystem services compared to other conventional farming methods. However, data on the impacts of rewilding on invertebrates remain scarce. Dung beetles contribute significantly to ecosystem function and are considered reliable indicators of ecological integrity. They have undergone serious population declines, largely due to changing agricultural practices. Dung beetles were sampled simultaneously at each of four sites for a total of 120 trapping days at each site. Two of the sites had been rewilded using large, free‐roaming herbivores, and two were nearby organic farms. The rewilding sites yielded greater species richness and abundance compared to organic farms. The abundance of dung beetles was more than 20 times greater at the rewilded sites compared to organic sites. One paracoprid (dung‐burying) species, Onthophagus similis, was particularly abundant, comprising 95% of all individuals at the rewilded sites. Nonetheless, captures at the rewilding sites remained significantly higher even after this species was omitted from the analysis. Practical implication: While additional research is necessary to ascertain whether our findings signify an atypical occurrence, the evidence from this case study suggests that rewilding with large herbivores may provide an effective strategy to combat dung beetle declines, restore ecological function and enhance ecosystem services.
... forestal. En contra, esta consiste en un proceso deliberado que inicia o acelera la recuperación de un ecosistema con respecto a su salud, integridad y sostenibilidad(Du Toit y Pettorelli, 2019: 2468 McDonald, Jonsons y Dixon, 2016: 2-13). Uno de los principales objetivos de los procesos restaurativos es revertir la erosión del suelo, imitando la estructura, función, diversidad y dinámica del ecosistema que se desea restaurar. ...
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Durante el transcurso de las últimas décadas, la comunidad científica y la sociedad civil han expresado su preocupación ante el incremento y la severidad de los incendios forestales, que amenazan y dañan gravemente los ecosistemas. En este contexto, es imperativo identificar y revisar críticamente la normativa que regula esta problemática, con el objeto de determinar si la legislación nacional aborda de manera adecuada la gestión de los incendios forestales en sus diversas dimensiones. Para ello, en este trabajo se realiza un análisis comparativo con el propósito de identificar deficiencias de nuestro ordenamiento jurídico, así como oportunidades de mejora. Finalmente, se formulan recomendaciones tendientes a fortalecer la gestión de los incendios forestales, que integran conocimientos y aportes de la ecología forestal en la materia, pues se estiman fundamentales para el diseño de estrategias de manejo forestal efectivas y sostenibles.
... While both seek to restore damaged ecosystems, rewilding generally focuses more on letting nature take its course once initial interventions are made. Rewilding also tends to lack historical benchmarks with which to measure a project's success, unlike restoration (du Toit and Pettorelli, 2019). This inherent indeterminacy necessitates continuous monitoring strategies to understand impacts over long timescales, ideally with an adaptive management approach to help determine the level of any ongoing interventions or management decisions (Perino et al., 2019;Carver et al., 2021). ...
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Introduction Rewilding, the facilitation of self-sustaining and resilient ecosystems by restoring natural processes, is an increasingly popular conservation approach and potential solution to the biodiversity and climate crises. Outcomes of rewilding can be unpredictable, and monitoring is essential to determine whether ecosystems are recovering. Metabarcoding, particularly of environmental DNA (eDNA), is revolutionizing biodiversity monitoring and could play an important role in understanding the impacts of rewilding but has mostly been applied within aquatic systems. Methods This systematic review focuses on the applications of eDNA metabarcoding in terrestrial monitoring, with additional insights from metabarcoding of bulk and ingested DNA. We examine publication trends, choice of sampling substrate and focal taxa, and investigate how well metabarcoding performs compared to other monitoring methods (e.g. camera trapping). Results Terrestrial ecosystems represented a small proportion of total papers, with forests the most studied system, soil and water the most popular substrates, and vertebrates the most targeted taxa. Most studies focused on measuring species richness, and few included analyzes of functional diversity. Greater species richness was found when using multiple substrates, but few studies took this approach. Metabarcoding did not consistently outperform other methods in terms of the number of vertebrate taxa detected, and this was likely influenced by choice of marker, sampling substrate and habitat. Discussion Our findings indicate that metabarcoding, particularly of eDNA, has the potential to play a key role in the monitoring of terrestrial rewilding, but that further ground- truthing is needed to establish the most appropriate sampling and experimental pipelines for the target taxa and terrestrial system of interest. Systematic Review Registration https://osf.io/38w9q/?view_only=47fdab224a7a43d298eccbe578f1fcf0 , identifier 38w9q.
... Rewilding is often considered a subset of ecological restoration, which is generally described as "assisting the recovery of a degraded, damaged, or destroyed ecosystem" (Corlett, 2016). Rewilding, on the other hand, is less committed to taxonomic precedent than restoration and encourages taxonomic substitutions for extinct native species (Toit and Pettorelli, 2019). Pettorelli et al. (2018) define rewilding as "the reorganization of biota and ecosystem processes to set an identified social-ecological system on a preferred trajectory, leading to the self-sustaining provision of ecosystem services with minimal ongoing management". ...
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Urban sustainability and food security remain pressing issues for cities across the world. Here, we argue that adapting rewilding to urban contexts unlocks new solutions for societal challenges. Rewilding is an established paradigm in ecological restoration, with the goal of restoring autonomous biotic and abiotic agents and processes. However, urban rewilding is an emerging but under-studied phenomenon that calls for multispecies coexistence and agency. Coupled with multispecies sustainability, urban rewilding can increase the operational autonomy of urban inhabitants through shared human-nonhuman co-stewardship of urban space. In this viewpoint paper, we explore the conceptual implications of rewilding for food security and land use planning across scales and infrastructures in urban settings. We then discuss how urban rewilding would particularly benefit food security across diverse urban contexts and examine some examples.
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Climate-smart rewilding is a promising approach to ecological restoration that combines the benefits of dynamic and process-based restoration with carbon sequestration for climate change mitigation. However, little is known about suitable locations for climate-smart rewilding in Europe as there is a lack of continental scale, spatial assessments of where to rewild. We present an approach to map the potential for climate-smart rewilding in Europe by considering three dimensions: (1) Ecological potential representing the best conditions for restoring key ecological processes, (2) Carbon potential describing the potential for carbon sequestration, and (3) Land potential reflecting the societal (opportunity) costs of dedicating land to rewilding. Using these three dimensions, we map the climate-smart rewilding potential across Europe and analyse synergies and trade-offs between them. Our findings show that the potential for climate-smart rewilding is scattered across Europe with hotspots predominantly found in mountainous regions, such as the Alps and the Scottish Highlands. The Iberian Peninsula, parts of Scandinavia, the North of the UK, and the East of Europe, also show opportunities for climate-smart rewilding. The patterns highlight that high potential is not equally distributed across European countries, adding complexity to the actual implementation of measures to reach restoration targets. Furthermore, high potential areas are often characterised by a high potential for one dimension, with limited synergies between the ecological, carbon and land potential dimensions, emphasising the tension between competing land demands. The approach presented here offers valuable input for planning processes and the exploration of future scenarios.
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Despite its importance as a key element for forest biodiversity and ecosystem functioning, uncertainties remain on how deadwood may change due to increasing forest dieback and subsequent management. The opportunistic cross-analysis of two large-scale, never-before-crossed forest databases, based on the spatially representative 16 × 16 km European grid, provided a dataset of 1804 plots in 17 countries with 10-year time series of annual measurements of tree defoliation followed by punctual assessment of deadwood volumes. Generalized linear mixed models and magnitude analyses quantified the relative influence of site environmental factors and 16 metrics of the current, recent and mid-term dynamics of local decline severity on plot-level deadwood volumes across European forests. The average level of dieback over the last five years and, to a lesser extent, the time elapsed since the last peak defoliation, were more important for deadwood stocks than were older levels of defoliation, the intensity or the frequency of extreme past declines. In Europe overall, total deadwood volume was 33% higher when the average level of decline over the previous five years increased by 10%. The significance and magnitude of the effects of past defoliation on deadwood were stronger in lowland forests than in upland forests, in coniferous forests than in broadleaf forests, in young stands than in mature stands, and for standing deadwood than for total deadwood, and varied with management. Retaining small, declining patches, excluded from salvage or sanitary logging within managed forests, could be an integrative opportunistic forestry tool for spontaneous restoration of deadwood.
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Facilitating “wildness” Humans have encroached upon a majority of Earth's lands. The current extinction crisis is a testament to human impacts on wilderness. If there is any hope of retaining a biodiverse planetary system, we must begin to learn how to coexist with, and leave space for, other species. The practice of “rewilding” has emerged as a method for returning wild lands, and wildness, to landscapes we have altered. Perino et al. review this concept and present a framework for implementing it broadly and in a way that considers ongoing human interaction. Science , this issue p. eaav5570
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Biologists energetically debate terminology in ecology and evolution, but rarely discuss general strategies for resolving these debates. We suggest focusing on metaphors, arguing that, rather than looking down on metaphors, biologists should embrace these terms as the powerful tools they are. Like any powerful tool, metaphors need to be used mindful of their limitations. We give guidance for recognizing metaphors and summarize their major limitations, which are hiding of important biological detail, ongoing vagueness rather than increasing precision, and seeming real rather than figurative. By keeping these limitations in mind, metaphors like adaptive radiation, adaptive landscape, biological invasion, and the ecological niche can be used to their full potential, powering scientific insight without driving research off the rails.
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Rewilding has been intensely debated among conservationists and ecologists. Multiple definitions and conceptual frameworks have been proposed for rewilding programmes, but hitherto all with a focus on promoting biodiversity conservation via restoration of ecological processes. Recently, however, it has been proposed to instead focus rewilding on the promotion of self-sustaining provisioning of preferred ecosystem services. Such shift in focus comes with an increased risk that rewilding efforts could be designed towards the promotion of simplified ecosystems providing selected ecosystem services, despite negative effects on biodiversity, as well as considerable socio-economic risks and ethical problems. We argue that rewilding should keep its focus on promoting biodiversity, with provisioning of other ecosystem services being integrated in the design of rewilding projects only as co-benefits. If such services become the main motivation for rewilding projects, there is a risk of misinterpretations and rewilding promoting less diverse ecosystems.
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Rewilding is emerging as a major issue in conservation. However, there are currently a dozen definitions of rewilding that include Pleistocene rewilding, island rewilding, trophic rewilding, functional rewilding and passive rewilding, and these remain fuzzy, lack clarity and, hence, hinder scientific discourse. Based on current definitions, it is unclear how the interventions described under the rewilding umbrella differ from those framed within the long-standing term 'restoration'. Even projects held up as iconic rewilding endeavours invariably began as restoration projects (e.g., Oostvaaderplassen; Pleistocene Park; the return of wolves to Yellowstone, etc.). Similarly, rewilding organisations (e.g., Rewilding Europe) typically began with a restoration focus. Scientific discourse requires precise language. The fuzziness of existing definitions of rewilding and lack of distinction from restoration practices means that scientific messages cannot be transferred accurately to a policy https://doi.
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Cambridge Core - Natural Resource Management, Agriculture, Horticulture and forestry - Rewilding - edited by Nathalie Pettorelli
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At a time when the science and practice of restoration ecology is adapting to ongoing environmental and social change, innovations in both methods and concepts are essential. Encouraging innovation means allowing open debate about alternative approaches that may add to the toolbox available for restoration. Such approaches are usually being examined as additions to, rather than substitutes for, traditional restoration practices. Recent debate has focused on the scope and intent of restoration as defined in documents such as the SER Standards. There is a mismatch between the default aim in the Standards of full restoration to a native reference system and the goals of international restoration efforts that have a broader and more functional focus. The next generation of restoration scientists and practitioners will need to navigate these issues to ensure that restoration remains effective and relevant. This will require, amongst other things, ongoing learning, sharing information and insights, humility, objectivity, continuous examination of assumptions and questioning current practices and perspectives. This article is protected by copyright. All rights reserved.