Tracks as a non-invasive tool for monitoring large carnivores

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Tracks as a non-invasive tool for monitoring large carnivores -Manon AUTHELET 13th October 2015 Journée d étude «Gestion rationnelle et conservation de la grande faune» Forest Resources Management (GxABT/Ulg) Master Thesis Supervisors : Pr. Cédric Vermeulen & Dr. Philippe Bouché

MONITORING CARNIVORES Low population densities Low reproductive rates High metabolic needs Large territories Carnivores populations decline around the world Ecological importance: at the top of food chains, regulating role Need for monitoring techniques! http://www.carnivore-namibia.org/ 2

MONITORING CARNIVORES Direct methods (direct observations): Questionnaires, interviews, and sighting reports (tourists, rangers, hunters,...) Harvest reports and pelt registration Road mortality samples Spotligt survey Catch-per-unit-effort Capture-mark-recapture (trap or remote camera) Transect, strip, or area sampling Radiotelemetry Photo: Miles Brown Photo: http://terriermandotcom.blogspot.be/ Photo: http://www.livemint.com/ Photo: comidayolas Photo: Mike Pflanz Photo: Northern https://whistlingforthejaguar.wordpress.com Pen BUT Carnivores are difficult to observe (and to catch) : low densities, elusive, often nocturnal Direct methods are expensive and invasive Samples are generally too small http://www.carnivore-namibia.org/ 3

MONITORING CARNIVORES Indirects methods (signs): Scent-station surveys Scat deposition transects Den and burrow surveys Vocalization response surveys Frequency of depredation complaints Hair or fecal analyses Track counts along a transect Photo: lifeforkresnagorge Ben Britton Photo: Catbreedspic Photo: Albert Herring Photo: http://illinois.edu/ Photo: www.tanzaniacarnivores.org/ BUT Need to correctly identify signs Need to check if signs density is correlated to animal density (other factors: vegetation, substrate, prey density, ) http://www.carnivore-namibia.org/ 4

MONITORING CARNIVORES TRACKS FOR COUNTING TRACKS FOR COUNTING TRACKS FOR TRACKS RECOGNITION FOR RECOGNITION PROSPECTS AND AND CONCLUSION Study Area Februray to May 2015 Hunting zones of Konkombouri (700 km²) and Pama Centre Sud (525 km²) in Burkina Faso W-Arly-Pendjari Complex Last viable populations of large carnivores in West Africa 5

Daniel Cuthbert Bruce Langton http://predatoraware.wildlifedirect.org/ Advantages of footprints Have been used for hundreds of years by a lot of indigenous people No need to observe or handle individuals Non invasive Less cost and field effort, better detection probability Work for rare, nocturnal or cryptic species Carnivores are known to use roads created by men Numerous potentialities : presence, activities, movements, range, abundance, sex, age, individual recognition... But track interpretation is subject to a lot of subjectivity Need for standardization http://www.carnivore-namibia.org/ 6

Improve indirect methods for the counting and the monitoring of large carnivores populations Large carnivores counting Perform the track counting of the large carnivores (lions, hyenas, cheetahs and wild dogs) to estimate their abundance Determine the effect of the sampling rate on the results precision to give recommandations Lion individuals recognition Generate orthophotos and Digital Elevation Model of lion footprints Identify measurable parameters allowing to uniquely identify an individual 7

Principle: Count tracks of large carnivores along sections of roads of known length (STANDER, 1998; FUNSTON et al., 2010) For all species: correlation between the «density» (IKA) of fresh tracks along transects and population density (FUNSTON et al., 2010). Sandy soils Clay soils 8

CARNIVORES MONITORING TRACKS FOR COUNTING TRACKS FOR COUNTING TRACKS FOR TRACKS RECOGNITION FOR RECOGNITION PROSPECTS AND AND CONCLUSION Results Estimates of lions, hyenas, leopards and cheetahs population abundance and density Effect of the sampling rate on the precision of the results: Number of transects = penetration rate (km/km²) Number of repetitions Boostrap Analysis: Resample for each possible sampling level Desired sampling rate when the CV reaches an acceptable level Mean Track Density CV = 20% Track density CV Sampling rate 9

Many facets of wildlife research demand the recognition of individuals in a population Natural features or tagging: Invasive, difficult for low density or rare species, expensive Tracks: Noninvasive, perfect for low density or reclusive species, cheaper 10

Some studies have tried to implement objective identification techniques for some felids (cougars, tigers, ) : Form Localization Of/made on the footprints Measurements Organization Wildtrack has invented a «Footprint Identification Technique» for the rhinoceros : Representation of a footprint with landmarks Series of measurements, constituting a geometric profile SOURCE: ALIBHAI, JEWELL & LAW (2008). 11

Lion footprint 3D reconstruction DEM 12

Goal: Find measurable parameters on orthophoto or DEM that allow to identify an individual: Vary the most for footprints of different individuals & Are as constant as possible for footprints of the same indivual 26 points placed manually on each footprint 161 measures / footprint: 115 linear measurements 36 angular measurements 5 areas 5 perimeters Statistical analyses 13

TRACKS FOR COUNTING TRACKS FOR RECOGNITION PROSPECTS AND CONCLUSION Results: Footprints of different individuals are sometimes more similar than footprints of the same individual Variability due to different identities + variability due to other factors (imprint conditions) Statistical analyses have not allowed to underscore some variables Sample was too small Variability could be too high in uncontrolled environment Need for a large training dataset of footprints of known individuals to appreciate within-individual variability 3D parameters are too variable and not linked to identity but to substrate depth and nature, behavior, slope, Not useful for the recognition but well for edge extraction 14

Track Counting Great accuracy if correct sampling rate Non-invasive Low cost Can be applied by local communities? Track recognition Operator effect Ok for relative abundance but need to use another method to construct the relationship between track density and absolute density for the study area Non-invasive Perspectives : CMR, individual monitoring, home range, movements, other species High within-individual varibility Tested in artificial conditions but doubts concerning its application in real conditions Heavy cost for the development of the method: need a big dataset and scientific expertise to build the algorithm Gain?! Subjectivity Need for automation Ihsaan Adams 15

Thank you for listening! Photo: Manon Authelet manon.authelet@gmail.com