class: center, middle, inverse, title-slide .title[ # Remote Sensing of Biodiversity ] .subtitle[ ## From Landscapes to Genes ] .author[ ### Jasper Slingsby ] .author[ ### & many others! ] .date[ ### MCB, UCT, 18 March 2026 ] --- class: center, middle ### We want to measure biodiversity everywhere, all the time... <img src="images/world_seasonality.gif" alt="" width="80%" style="display: block; margin: auto;" /> .center[Remote sensing is pretty much the only way this can be achieved...] --- layout: false .pull-left[ ## It's a rapidly growing field <img src="images/turner2003.png" alt="" width="90%" style="display: block; margin: auto auto auto 0;" /> <img src="images/satellitelaunches.jpg" alt="" width="90%" style="display: block; margin: auto auto auto 0;" /> .footnote[Turner et al. 2003] ] .pull-right[ <img src="images/cavenderbares2020.png" alt="" width="75%" style="display: block; margin: auto auto auto 0;" /> .footnote[Cavender-Bares et al. 2020] ] --- layout: false <img src="images/bioscape_new.png" alt="" width="100%" style="display: block; margin: auto;" /> .left[.footnote[...and the Cape is currently the epicentre of this endeavour | www.bioscape.io]] --- layout: false ## BioSCape: Biodiversity Survey of the Cape .pull-left[ - NASA's first biodiversity-focused field campaign - `\(>\)` 150 scientists and conservation practitioners - 19 teams (mixed US, RSA, other) - fundamental and applied science - terrestrial and aquatic - 3 planes - 6 instruments (2 x V-SWIR imaging spectrometers, hyperspectral thermal, multispectral (RGB + NIR) and 2 x LiDAR) <img src="images/bioscape_kumu_hex.png" alt="" width="100%" style="display: block; margin: auto;" /> ] .pull-right[ <img src="images/bioscape_planes_portrait.png" alt="" width="95%" style="display: block; margin: auto;" /> .footnote[www.bioscape.io] ] --- class: center, middle <img src="images/Bioscape infographic_e3.jpg" alt="" width="100%" style="display: block; margin: auto;" /> --- class: center, middle ## The technology --- background-image: url("images/nasa_ems.jpeg") background-size: contain text-color: white .left-column[ ## .my-style-white[The Electromagnetic Spectrum] ] --- .left-column[ ## Sensor types Active vs passive Multispectral vs hyperspectral Variation within each type around spectral range and resolution, spatial resolution, revisit time, etc .footnote[[Pettorelli et al. 2018](http://dx.doi.org/10.13140/RG.2.2.25962.41926)] ] .right-column[ <img src="images/pettorelli2018_sensors.png" alt="" width="100%" style="display: block; margin: auto;" /> ] --- layout: false ## Multispectral vs hyperspectral (imaging spectrometers) <img src="images/multi vs hyper.png" alt="" width="70%" style="display: block; margin: auto;" /> --- layout: false .pull-left[ ## Light detection and ranging (LiDAR) <img src="images/peninsula_lidar.png" alt="" width="100%" style="display: block; margin: auto;" /> Proteaceae shrubs (dark green) surrounded by low shrubs, forbs and graminoids at Silvermine, TMNP. .footnote[Data from City of Cape Town] ] .pull-right[ <img src="images/purkis_klemas2011_lidar.png" alt="" width="100%" style="display: block; margin: auto;" /> Light detection and ranging (LiDAR) uses active remote sensing by firing a "laser beam" to measure topography and the vertical structure of vegetation. .footnote[Purkis and Klemas 2011] ] --- ### These are just numbers and not useful without ground observations <img src="images/turner2014.jpeg" alt="" width="75%" style="display: block; margin: auto;" /> .footnote[[Turner 2014](https://doi-org.ezproxy.uct.ac.za/10.1126/science.1256014)] --- class: center, middle ## But what are we trying to measure? --- layout: false .pull-left[ ## There are many facets of biodiversity! <br> Each facet provides its own challenges and opportunities and require different methods of remote sensing. ] .pull-right[ <img src="images/Noss_Biodiversity.png" alt="" width="100%" style="display: block; margin: auto;" /> .footnote[Noss 1990, _Conservation Biology_] ] --- layout: false .pull-left[ ## There are many facets of biodiversity! An advantage of remote sensing is that it can directly measure the structure, composition and function of biodiversity... <img src="images/skidmore2021_fig1.png" alt="" width="120%" style="display: block; margin: auto;" /> .footnote[Skidmore et al. 2021] ] .pull-right[ <img src="images/ebv_circle.png" alt="" width="90%" style="display: block; margin: auto;" /> ...at least from the scale of individuals up... .footnote[https://geobon.org/] ] --- class: center, middle ##Multispectral remote sensing --- class: center ##Productivity and Seasonality <img src="images/world_seasonality.gif" alt="" width="80%" style="display: block; margin: auto;" /> --- class: center ##Land cover (and change) <img src="images/skowno2021.jpg" alt="" width="50%" style="display: block; margin: auto;" /> .left[.footnote[Skowno et al. 2021]] --- class: center ##Land cover change detection <img src="images/renosterveld_planet.gif" alt="" width="70%" style="display: block; margin: auto;" /> .left[.footnote[Moncrieff 2022]] --- class: center ##Land cover change time series <img src="images/moilwe.png" alt="" width="60%" style="display: block; margin: auto;" /> .left[.footnote[Moilwe et al. in prep]] --- class: center ## But there are challenges and limitations... <img src="images/schimel2020_scale.png" alt="" width="50%" style="display: block; margin: auto;" /> .left[.footnote[Schimel et al. 2020]] .pull-right[.footnote[The mixed pixel problem...]] --- class: center, middle ## What about hyperspectral data? --- class: center ## Spectral unmixing can detect "spectral signatures" .left-column[ <img src="images/jonaskop_class.png" alt="" width="100%" style="display: block; margin: auto;" /> .smaller[Jonaskop, Riviersonderend Mountains] ] .right-column[ Map species/types based on their reflectance of the electromagnetic spectrum! <img src="images/jonaskop_spectral_library.png" alt="" width="50%" style="display: block; margin: auto;" /> Given a library of spectral signatures of different species and land cover types (endmembers), spectral unmixing infers the composition of each pixel from the possible mixes of endmembers. This gives a cover map of the majority endmember for each pixel (as here) and the fraction of each endmember for all pixels (next slide). ] --- class: center ## Spectral unmixing can detect "spectral signatures" <img src="images/jonaskop_unmix.png" alt="" width="100%" style="display: block; margin: auto;" /> .left[.footnote[Fractional cover of species (e.g. pines), functional groups or land cover types! ]] --- layout: false .pull-left[ ## Mapping traits... Imaging spectroscopy ("hyperspectral" remote sensing) allows direct measurement of leaf traits. <img src="images/cawse2021_spectra.png" alt="" width="92%" style="display: block; margin: auto auto auto 0;" /> ] .pull-right[ <img src="images/peninsula_hyperspec.png" alt="" width="100%" style="display: block; margin: auto;" /> ] --- layout: false <img src="images/traitmapping.png" alt="" width="100%" /> --- ## Potential uses of trait maps? .pull-left[ <img src="images/ashleigh.png" alt="" width="70%" style="display: block; margin: auto;" /> Using trait maps to infer the legacy impacts of invasive alien plants. ] .pull-right[ <img src="images/sam.png" alt="" width="70%" style="display: block; margin: auto;" /> Using traits to map landscape flammability. ] --- class: center, middle ## Very high resolution multispectral data? --- layout: false .pull-left[ ## The Clanwilliam Cedar An iconic critically endangered species... <img src="images/cedars_pic.png" alt="" width="100%" style="display: block; margin: auto;" /> ] .pull-right[ <img src="images/cedar_door.jpg" alt="" width="62%" style="display: block; margin: auto;" /> ] .footnote[Historically overharvested for timber, but still declining despite protection.] --- layout: false .pull-left[ ## The Clanwilliam Cedar <img src="images/cedars_mapped.png" alt="" width="100%" style="display: block; margin: auto;" /> Manual mapping from 50cm RGB aerial imagery (2013) .footnote[] ] .pull-right[ <img src="images/CederbergMap.jpeg" alt="" width="92%" style="display: block; margin: auto;" /> 13,419 cedar tree localities!!! .footnote[Slingsby Maps - _Hike the Cederberg_] ] --- layout: false ## The Clanwilliam Cedar .pull-left[ <img src="images/slingsby2019title.png" alt="" width="100%" style="display: block; margin: auto;" /> <img src="images/slingsby2019full.png" alt="" width="100%" style="display: block; margin: auto;" /> .footnote[] ] .pull-right[ Field validation: - Typically only adult trees or clumps with >4m `\(^2\)` live canopy were reliably identified from aerial imagery, so many smaller individuals are missed. - The majority of trees were dead, but these were not apparent in the imagery. - Trees that had recently died (dead leaves still present) outnumbered live trees by a ratio of 2:1. <br> Useful baseline and suggestive of rapid change, but couldn't be used to investigate change over time. .footnote[Slingsby and Slingsby 2019, _PeerJ_] ] --- layout: false .pull-left[ ## The Clanwilliam Cedar <img src="images/jess.jpg" alt="" width="100%" style="display: block; margin: auto;" /> Cedar decadal resurvey with 2022 imagery... .footnote[Jessica Prevôst, Honours thesis] ] .pull-right[ <img src="images/cedar_points_plot_legend_inside.png" alt="" width="85%" style="display: block; margin: auto;" /> ] --- ## The Clanwilliam Cedar <img src="images/cedarresultsoverview.png" alt="" width="90%" style="display: block; margin: auto;" /> --- ## The Clanwilliam Cedar - correlates of mortality? <br> Mortality ~ Environmental variables? -- <br> BUT WAIT! This is the basis of species distribution modelling... Since trees only die where they occur, all we're going to get is the distribution of trees, not the distribution of tree mortality... --- ## The Clanwilliam Cedar - correlates of mortality? .pull-left[ <img src="images/eisaguirre2025.png" alt="" width="100%" style="display: block; margin: auto;" /> A Bayesian thinned spatial point process (SPP) modelling framework that couples occurrence with a mortality process to formally treat mortality events across the landscape as a spatial process. Developed for modelling animal mortality within their known habitat use based on telemetry data. .footnote[Eisaguirre et al 2025] ] .pull-right[ <img src="images/cedarmodel.png" alt="" width="100%" style="display: block; margin: auto;" /> - Joint model of occurrence and mortality - 30m digital elevation model (DEM) - CapeNature fire records - CHELSA downscaled reanalysis climate data ] --- ## The Clanwilliam Cedar - correlates of mortality? <img src="images/cedarmodelmaps.png" alt="" width="75%" style="display: block; margin: auto;" /> .footnote[Prevôst and Slingsby _in prep_] --- ## The Clanwilliam Cedar - correlates of mortality? .pull-left[ <img src="images/cedarmodelfire.png" alt="" width="80%" style="display: block; margin: auto;" /> .footnote[Prevôst and Slingsby _in prep_] ] .pull-right[ <img src="images/cedarmodelmat.png" alt="" width="80%" style="display: block; margin: auto;" /> ] --- .pull-left[ ## The Clanwilliam Cedar ### Conclusions and limitations - Alarmingly high mortality (>17% in a decade)! - Mortality is associated with greater numbers of fires and faster warming BUT... - Climate data were coarse (1km) - Still to include field validation <br> Sadly, ±90% of the Cederberg burnt in the past year, so likely that many more trees have died... ] .pull-right[ <img src="images/cedarboys.jpg" alt="" width="80%" style="display: block; margin: auto;" /> ] --- layout: false ## Mapping cedars with Lidar? .pull-left[ <img src="images/bioscape_cedars_driehoek_rgb.png" alt="" width="100%" style="display: block; margin: auto;" /> ] .pull-right[ <img src="images/bioscape_cedars_driehoek_lvis.png" alt="" width="100%" style="display: block; margin: auto;" /> ] .footnote[De Rif cedar plantation above Driehoek | www.bioscape.io/data] --- class: center, middle ## Mapping cedars with hyperspectral imagery? --- layout: false ## Mapping genotypes with hyperspectral imagery? .pull-left[ <img src="images/czyz2020.png" alt="" width="100%" style="display: block; margin: auto;" /> A bit of a holy grail for remote sensing of biodiversity is to be able to map genetic variation, which would be a game changer for conservation and evolutionary biology. .footnote[Czyż et al. 2020, _Ecology and Evolution_] ] .pull-right[ <img src="images/cedarvariants.jpeg" alt="" width="100%" style="display: block; margin: auto;" /> .footnote[Some cedar colour morphs... Genotypes?] ] --- layout: false ## Mapping cedars with hyperspectral imagery? .pull-left[ <img src="images/spectrometer.jpg" alt="" width="55%" style="display: block; margin: auto;" /><img src="images/cedarspectra.png" alt="" width="55%" style="display: block; margin: auto;" /> .footnote[Leaf level spectra show promising differences between morphs.] ] .pull-right[ <img src="images/cedarunmixing.png" alt="" width="98%" style="display: block; margin: auto;" /> .footnote[Mapping from imagery does not (Prevôst 2025, _Honours_).] ] --- layout: false ## Mapping _**milkwoods**_ with hyperspectral imagery .pull-left[ <img src="images/milkwoodleaves.png" alt="" width="40%" style="display: block; margin: auto;" /><img src="images/milkwooddistribution.png" alt="" width="40%" style="display: block; margin: auto;" /><img src="images/milkwoodunderstorey.png" alt="" width="40%" style="display: block; margin: auto;" /> <br> ] .pull-right[ <img src="images/ANG_Agulhas.png" alt="" width="100%" style="display: block; margin: auto auto auto 0;" /> - Easier to measure (leaf and canopy) - Larger distribution (and potential for variation) - Extensive hyperspectral imagery from BioSCape .footnote[Tallulah Glasby (PhD student)] ] --- class: center, middle # Thanks! More at www.plantecolo.gy and www.bioscape.io