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Ecology and Evolution. 2023;13:e10671.
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1 of 6
https://doi.org/10.1002/ece3.10671
www.ecolevol.org
Received:29Augus t2023
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Revised:13O ctobe r2023
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Accepted :16Octobe r2023
DOI:10.1002 /ece3.10671
NATURE NOTES
A novel record of African wild dogs (Lycaon pictus) in Vwaza
Marsh Wildlife Reserve, Malawi
Olivia Sievert1,2 | Matthias Hammer3 | Eleanor Comley1 | Benjamin Hintz1 |
William O. Mgoola4 | Robert S. Davis5
This is an op en access arti cle under the ter ms of the CreativeCommonsAttributionL icense,whichpe rmitsuse,dis tribu tionandreprod uctioninanymed ium,
provide dtheoriginalwor kisproperlycited.
© 2023 The Authors . Ecology and Evoluti onpublishedbyJo hnWiley&S onsLtd.
1Lilong weWildlifeTrust,Lilong we,Malawi
2Endange redWildlifeTrust ,Midrand,
SouthAf rica
3BiosphereExp editions,Dublin,Ireland
4Depar tment of Nationa l Parks and
WildlifeMalawi,Lilongwe,Malawi
5Department of Conservation
Management,NelsonMandelaUniversity,
George ,WesternCape,S outhAf rica
Correspondence
OliviaSievert,LilongweWildlifeTrust,
Kenyatt aRoad,P OBox1464,L ilong we,
Malawi.
Email: olivia.sievert@gmail.com
Abstract
Most Africanwild dog (Lycaon pictus)populations are indecline and,due to habitat
fragmentation and conflict rates in areas of higher anthropogenic land-use, are pri-
marilyrestrictedtoprotectedareas.Asaspeciesthatoccursatlowdensities,witha
strictreproductivesocialstructure,wilddogsrelyonlong-rangedispersaltofacilitate
colonization,reproduction,andpackformation.InMalawi,largecarnivoreshavebeen
subjecttowidespreadpopulationdeclineandseveralprotectedareashaveareduced
large carnivore guild, including the loss of resident wild dog populations. Here, during
abiodiversitymonitoringcameratrapsurvey,wecapturedanovelrecordofwilddogs
inVwazaMarshWildlifeReserve(Vwaza),Malawi.The11photographiccapturesof
potentiallythreeindividualwilddogsrepresentthefirstdocumentedevidenceofthe
species in Vwazaand the first recordsincean unconfirmed report in 2011.Wehy-
pothesizethatthisgroupofwilddogsmovedintoVwazathroughtheMalawi-Zambia
Transfrontier Conservation Area (MZTFCA), with the MZTFCA linking protected
areasinMalawi with theLuangwaValley,Zambia.Theevidence providedhere, and
similardocumentationinKasunguNationalPark,Malawi,showthatlarge carnivores
canpotentiallymovethroughtheMZTFCAintoprotectedareasinMalawi.Weargue
thattheMZTFCA providesanimportantdispersalcorridor that could helpfacilitate
the recolon ization of wild dogs, a nd other large car nivores, in Malawia n protected
areas.However,further researchisneeded toassess the permeabilityandstatus of
theMZTFCAcorridorintoMalawi.Weshowthatcameratrapscanbeusefultodocu-
mentnovelrecordsofrarespeciesandcanbeusedtoinformconservationmanage-
ment planning.
KEYWORDS
cameratraps,dispersal,largecarnivores,Malawi,Zambia
TAXONOMY CLASSIFICATION
Appliedecology,Biodiversityecology,Conservationecolog y,Movementecology,Restoration
ecology
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SIEVERT et al.
1 | INTRODUCTIO N
The A f r i c a nwildd o g ( Lycaon pictus; hereafter wi ld dog) is classifie d as
endangered,withapproximately1400breedingindividualsremain-
ing across 39 subpopulations (Woodroffe & Sillero-Zubiri, 2020).
Once wide spread across Sub -Sahara n Africa, wild dog s have lost
approximately93.2%oftheirhistoricalrange(Wolf&Ripple, 2017 )
with habitat fragmentation, humanpersecution and infectious dis-
ease as the p rimary dri vers of their conti nued populati on decline
(Woodroffe&Sillero-Zubiri,2020).Asaresult,viablewilddogpop-
ulationsarelargelyrestrictedtoprotectedareas(Cozzietal.,2020;
Woodroffe&Sillero-Zubiri,2020). The relative isolation of wild dog
subpopu lations, com bined with t heir low popu lation densi ties and
strict reproductive social structure, means the species is par ticu-
larlyreliantondispersalforcolonization,packformation,andrepro-
ductio n (Cozzi et al., 2020; Woo droffe et al. , 2020). Further more,
their large spatial requirements, especially during the dispersal
stage, mean they of ten stray beyond protected area boundaries
andintoconflictwithhumans(vanderMeeretal.,2014;Woodroffe
et al., 20 07).
Malawi, in s outh-centr al Africa , has undergo ne a signific ant de-
cline in lar ge carnivore pop ulations (Davis et al., 2021; Mésochina
et al., 2010; Munt hali & Mkanda, 2002). Severe und er-fu nding for
conservation and park management, combinedwith increasing an-
thropogenic pressures around park boundaries, has resulted in pro-
tected areas being subject to high levels of poaching and habitat
destruction (Munthali & Mkanda, 2002; van Velden et al., 2020).
Particularlyforwide-ranging,social,andless-crypticspecies,suchas
wilddogandlion(Panthera leo),thelossof abundantpreybasesand
edge effects surrounding protected areas have led to near-extirpation
within Malawi (Daviset al.,2021;Mésochina et al., 2010 ; Purchase
et al., 20 07).Althoughsomeparksunderpublic–privatepartnerships
have begunto recoverlarge carnivore populations through translo-
cation and reintroduction projec ts (e.g., Briers-Louw et al., 2019;
Sievert ,Fattebert,etal.,2022),mostofMalawi'sprotectedareasare
reliant on corridor protection, reserve restoration, and natural recolo-
nization to increase large carnivore populations. As several protected
areas in Malawi have transboundary initiatives with the Luangwa
ValleysysteminZambia,theyareoptimalareasfordispersalandpo-
tentialrecolonization(Davisetal.,2021;Sievert,Evans,etal.,2022).
FIGURE 1 MapshowingthelocationofVwazaMarshWildlifeReser ve(Vwaza)anditspositionwithinthewiderMalawiZambia
TransfrontierConser vationArea(MZTFCA).Inset(a)displaystheloc ationofcameratrapsdeployedinVwazaduringthesurveyand(b)
displaysthelocationoftheMZTFCAinsouth-centralAfrica,withtheMZTFCAhighlighted.
20457758, 2023, 11, Downloaded from https://onlinelibrary.wiley.com/doi/10.1002/ece3.10671 by South African Medical Research, Wiley Online Library on [01/11/2023]. See the Terms and Conditions (https://onlinelibrary.wiley.com/terms-and-conditions) on Wiley Online Library for rules of use; OA articles are governed by the applicable Creative Commons License
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SIEVERT e t al.
Here, usin g data from a recent c amera trap s urvey, we docu-
mentanovelrecordofagroupofwilddogsinVwazaMarshWildlife
Reserve (hereafter Vwaza), Malawi. Although considered part
of the current wild dog distribution range (Woodroffe & Sillero-
Zubiri,2020),evidenceofthespecies'status inVwazaisextremely
limited, with the last unconfirmed report in 2011 (Department
of National P arks and Wil dlife, 2011). As such, these images rep-
resent the first photographic evidence of wild dogs in Vwaza. We
discuss the significance of this result for large carnivore recoloni-
zationinMalawiandthepotentialimplicationsforconnectivityand
dispers al corridors across the wid er Malawi-Zambia Transfront ier
Conser vationArea(MZTFCA).
2 | METHODS
2.1 | Vwaza Marsh Wildlife Reserve and
Malawi-Zambia Transfrontier Conservation Area
This study was conducted in Vwaza Marsh Wildlife Reser ve,
Malawi(33°28′ E,11°00′ S;986 km2). The reserve consists primar-
ilyofm io mbo wo o dl and (Brachystegia spp.), interspersed with wet-
landareas that are seasonally flooded bythe Luwewe and South
Rukururivers(Engel etal.,2013;Mgoola&Msiska, 2017). Vwaza
formspartofthe32,278 km2MZTFCA(Figure 1), a significant area
for biodiversity conservationin the Central Zambezian Miombo
Woodland Ecor egion that was e stablis hed in 200 3 (Peace Park s
Foundation, 2023). The MZTFCA consists of Vwaza, Kasungu
National P ark and Nyika Nati onal Park in Malawi an d Lukusuzi
National Park, North Luangwa National Park and several game
manageme nt and forest res erve areas in Zam bia. The MZTFC A
is split into t wo main component s, with Vwaza, which border s
Lundazi Forest Reserve in Zambia, forming part of the Nyika-
NorthLuangwaTFCA .
2.2 | Camera trap surveys
A total of 17 infrared camera traps (16 Bushnell Trophy Cam;
Bushnell Corporation; 1 Reconyx HyperFire; Reconyx) were de-
ployed acro ss the southe rn section of Vw aza (Figure 1a), with an
average trap spacing of 1.38 km (SD ± 0.96). Three camera traps
were baited with goat carcasses to increase carnivore detection
rates, as one ofthekeyobjectivesof the sur veywastoprovide an
inventoryofcarnivoresinthe park.Cameraplacementfocusedon
the southern sec tion of the park due to the limited road net work in
thenorth.As large carnivoreswereakeyfocus ofthe biodiversity
survey, cam era traps wer e primarily p laced along th e Vwaza road
networ k to maximize detec tion rates (Davis e t al., 2021). Camera
traps were attached to trees ~80 cm above the ground and facing
the road. Camera traps were programmed with the same settings
(16MP image size, 10 s inter val, medium s ensitivity, med ium night
vision shut ter speed),and took twoimages consecutively,allowing
formorereliablecapturesofmultipleindividualsinherdsorgroups.
Cameratraps were originallysetupduring a Biosphere Expedition
citizensciencebiodiversitymonitoringproject(September25,2022
–October 07,2022), with the 14 non-baited camerasleft in place
untilOctober22,2022.AllpictureswereanalyzedusingTimelapse2
(v2.3.0.0; Greenberg, 2019). Images of individual wild dogs were
identifiedtotheindividual-levelwherepossible,usinguniquepelage
patterns and timestamp information.
3 | RESULTS
Duringthesurvey,11imagesof wilddogswereobtainedfrom four
different observation events at three camera stations. Individual
identificationfrompelagepatternsandestimates ofthenumber of
wild dogs observed in Vwazawere limited by the quality of infra-
redimages. Fromleft flankimages,wecouldidentifytwodifferent
individuals (Figure 2). Right flank images were harder to identify
(Figure 3); however, from the series of timestamps on three pho-
tograph ic captures ther e was evidence that pote ntially three dif-
ferent wild dogs moved past the camera trap in quick succession.
Therefore, we are confident there were a minimum of two individual
wilddogs,withathirdindividuallikelybasedontimestampsandpo-
tential variation in pelage patterns. All photographic captures were
recordedatnightbetween06:47p.m.and04:13a.m.
FIGURE 2 Cameratrapimagesofleftflankpelagepatternsthat
identif ytwoindividualAfricanwilddogsinVwazaMarshWildlife
Reserve,Malawi.PanelaisfromSeptember24,2022,thefirst
documentedimagesofthespeciesinthereserve.Panelbisfrom
October04,2022atadifferentcameratrapstation.
20457758, 2023, 11, Downloaded from https://onlinelibrary.wiley.com/doi/10.1002/ece3.10671 by South African Medical Research, Wiley Online Library on [01/11/2023]. See the Terms and Conditions (https://onlinelibrary.wiley.com/terms-and-conditions) on Wiley Online Library for rules of use; OA articles are governed by the applicable Creative Commons License
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SIEVERT et al.
4 | DISCUSSION
Through ourcamera trapsurvey,wehaveconfirmedthefirstpho-
tographic records of wild dogs in Vwaza and provided evidence that
wilddogs are stillpresent, thoughlikely transient, in the protected
area. Ou r findings suppo rt Davis et al. (2021), who reported the
presence of dispersing wild dogs and lions in Kasungu National Park
(KNP),Malawi,andattributedthistodispersalcorridorsthroughthe
MZTFC A. Encoura gingly, we documente d a group of at least t wo
wild dogs in Vwaza, whereas the same single wild dog, confirmed
through pelage patterns, was recorded in KNP during camera trap
surveys in2017and2018(Davis et al., 2021). As camera trap sur-
veys have previously taken place in Vwaza in 2018 and 2019(see
Harwood et al., 2019, 2020),andthere have beennoobservations
from park management since the time of this survey (Matthews
Mumba,personalcommunication),itisunlikelythegroupisresident.
Itis t her efo r ea ssu m edt h at t hiswa sei t her adi spe r s alg rou pco ntai n-
ingcohortsofasinglesexorasplinter-groupfromtheZambian-side
ofthe MZTFC A. We feelthis conclusion is reasonable,becauseof
theproximit yoftheLuangwaValleyandthisregionholdingthelarg-
estwilddogpopulationinZambia(Creeletal.,2020).Ourwilddog
imagesfromVwazawerecross-referencedwithawilddogdatabase
maintainedby Zambia Carnivore Program that encompasses parts
oftheMZTFCA,butcouldnotbelinkedtoknownindividualsinthe
database(Matthew Becker,personal communication). However,as
this database is missing individuals thatreside outside of the core
protect ed areas and ac knowledgin g the low qualit y of the images
provided for identification, it is still probable that these wild dogs
movedintoVwazafromtheZambian-sideoftheMZTFCA.
Wilddogs requirelargeareasofconnectedhabitat and oftenex-
hibit long-r ange dispersal eve nts, with such move ments promoting
source-sinkdynamicsbyfacilitatingrecolonizationandsupportingvi-
ablepopulationsatnationalandinternationalscales(Cozzietal.,2020;
Creel et al., 2020). As there was no evidence of wild dog pups in these
images, toward the end of the denning season (May–September;
Comleyetal.,2023), andconsideringthesizeoftheobser vedgroup,
we beli eve i ti s lik elyt h eV w a zai m age s are ofa dis p e r sal g rou p ors p lin-
terpack .OurevidenceofawilddoggroupinVwaza,alongsidesimilar
findingsinKNP(Davisetal.,2021), suggests that recolonization, or at
leastsupplementation,of Malawi'sprotectedareasfromsourcepop-
ulationsintheMZTFC A,orwithincloseproximit y(LuambeNP,North
LuangwaNP,SouthLuangwaNP),couldbe possible.Webelieve that
management initiatives are needed to increase law enforcement and
restorepreybasestoabundantlevelsintheseprotectedareas,asthe
issuesofpoachingandinsufficientpreynumberswillhinderdispersal
andsubsequentrecolonizationefforts(DNPW,2011).
Anthropogenicland-use, particularlythe intensity ofhuman ac-
tivities,hasbeenidentifiedasthekeyfactorinfluencingconnectivity
and landscape permeabilityfor wilddogs (Cozzi et al.,2020; Creel
et al., 2020; Hofmann et al., 2021). As the human footprint index in-
creasesaroundtheMZTFCA(Creeletal.,2020;Watsonetal.,2015),
these pressures mayhinder future dispersal attempts and further
FIGURE 3 Fourcameratrapimages
of African wild dogs at the same camera
trapstationinVwazaMarshWildlife
Reserve,Malawi.(a)Thefirstrecorded
imageofawilddog(18October2022);
(b)thefollowingimageandfromthe
time stamp and the difference in pelage
patterns,webelievethisislikelytobea
secondindividual;(c)adifferentindividual
fromb,basedonpelagepatternsandthe
timestamp;(d)animagefromthesame
cameratrapstation(Oc tober19,2022);it
isdifficulttosaywithcert aintyifthisisa
newindividualbasedonright-flankpelage
patterns.Fromtheseimages,wesuggest
thattherewerelikelythreeindividualwild
dogs in Vwaza during the camera trap
surv ey.
20457758, 2023, 11, Downloaded from https://onlinelibrary.wiley.com/doi/10.1002/ece3.10671 by South African Medical Research, Wiley Online Library on [01/11/2023]. See the Terms and Conditions (https://onlinelibrary.wiley.com/terms-and-conditions) on Wiley Online Library for rules of use; OA articles are governed by the applicable Creative Commons License
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SIEVERT e t al.
researchisneededtoassessconnectivityandpermeabilitybetween
Malawianprotectedareasandpotentialdispersalcorridors.Thedis-
tance between potential source populations in Zambia (<30 0 km)
and Vwaza is within the limits of known wild dog dispersal ranges, so
establishingifthelackofrecordeddispersaleventsisduetoinsuffi-
cientmonitoringinMalawi'sprotectedareasorbarrierstodispersal
along MZTFCAmovement corridors is an essential step for conser-
vationplanning.Astherehavebeenunconfirmedwilddogreportsin
Mal awian prote ctedareasovert helas tfewy ears ,itisimp or t antth at
observationsareproperlyreported,andthattrainingisprovidedfor
co rrec t ide n tif i c ati o na n dre p or tin gstan d ard s .Ween cour a gef ur the r
reporting of novel dispersal events for threatened large carnivores
andsugges tthatt heMZTFCAcou ldp rov ideavalua blecon servation
toolforrestoringlargecarnivoresinMalawi'sprotectedareas.
AUTHOR CONTRIBUTIONS
Olivia Sievert: Conceptualization (equal); methodology (equal);
project administration (equal); writing – original draft (support-
ing); writing – review and editing (equal). Matthias Hammer:
Conceptualization(equal);datacuration(supporting);methodology
(equal); project administration (equal); writing – review and edit-
ing (supporting). Eleanor Comley:Datacuration(supporting);writ-
ing–reviewandediting(equal).Benjamin Hintz: Conceptualization
(equal); dat a curation (lead); methodology (equal); project admin-
istrat ion (equal). William O. Mgoola: Writing – revi ew and editin g
(equal).Robert S. Davis:Visualization (lead);writing–originaldraft
(lead);writing–reviewandediting(equal).
ACKNOWLEDGMENTS
FundingwasprovidedbyBiosphereExpeditionsthroughtheirpar tici-
patory citizen sciencemodel.Wethank the Department of National
Parks an d Wildlife Malawi and t he Vwaza Marsh Wildlife Reserve
managementteamandrangersfortheirsupportandcontinuedcollab-
oration.We thankalltheBiosphereExpedition citizenscientists and
staffwhoparticipatedinthisstu dy.Wearegratef ultothetwoanony-
mousreviewerswhoprovidedvaluablefeedbackonthismanuscript.
CONFLICT OF INTEREST STATEMENT
The authors declare no competing interests.
DATA AVAIL AB I LI T Y STATE MEN T
Wilddogimagesare presentedinthemanuscript. Nocodingorad-
ditionalanalyseswereconducted.
ORCID
Olivia Sievert https://orcid.org/0000-0003-3091-7592
Robert S. Davis https://orcid.org/0000-0002-9953-1340
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