I am reflecting on climate-coupled evolution—the idea that rapid environmental change synchronously reshapes species’ geographic ranges, selects for stress-tolerant traits and scrambles gene pools through new contact zones and human seed movements. Banksia (Proteaceae) is a powerful lens for this concept because its radiation is tightly linked to fire, drought and nutrient-poor soils—pressures that are all intensifying in 21st-century Australia. By synthesising recent species-distribution modelling, eco-physiological experiments, fire-demography studies and conservation-genomic trials, I can make evidence-grounded predictions about how the genus is likely to evolve as the continent warms and dries.
1 | Range will contract and shift
MaxEnt projections for 18 south-western taxa show median habitat losses of 30–80 % by 2070, with climatically suitable refugia retreating to cooler, wetter pockets near the south coast and upland granite outcrops (Figure 1). Obligate seeders with poor dispersal (e.g. B. cuneata) are the most vulnerable, whereas broad-niche resprouters (e.g. B. attenuata) can track climate envelopes upslope or poleward (Fitzpatrick et al., 2008).
2 | Drought will favour tougher hydraulics
Common-garden and field physiology work in the South-West Australian Floristic Region reveals large, heritable variation in water-use efficiency, leaf thickness and xylem safety among co-occurring Banksia species. Dry-origin genotypes deploy narrower vessels and smaller, denser leaves—traits already linked to higher survivorship under experimental drought. As rainfall continues to decline by up to 60 % in winter–spring, these alleles should rise in frequency, shifting population means toward more conservative hydraulic architectures (Cochrane et al., 2014).
3 | Shorter fire cycles will retune life histories
Obligate seeder shrubs such as B. hookeriana and B. cunninghamii need 12–15 years to rebuild canopy seed banks. Spatially explicit fire-demography models show local extinction risk exceeds 80 % when fires recur more frequently. Two evolutionary trajectories are plausible: (i) selection for earlier age at first flowering, shortening the juvenile phase, and (ii) genetic introgression of lignotubers, shifting some lineages from strict seeding to facultative resprouting (Arthur Rylah Institute, 2024).
4 | Hybrid zones will accelerate adaptive change
Climate-driven range shifts and disturbance are already bringing previously allopatric lineages into contact. Morphometrics and AFLP markers have confirmed a hybrid swarm between B. hookeriana and B. prionotes in a disturbed coastal heath, whereas undisturbed sites show sharp species boundaries. Such hybridisation can shuffle drought- and frost-tolerance alleles faster than mutation alone, potentially generating novel morphotypes suited to emerging niches (Lamont et al., 2003).
5 | People will become part of the evolutionary machinery
Restoration programs in Victoria and Western Australia increasingly use “climate-adjusted provenance” mixes that blend local seed with material from hotter or drier analogues. Trial plots (‘Climate Future Plots’) are monitoring fitness effects across decades; early results suggest provenance mixing increases recruitment under heatwave conditions. Because Banksia retains high standing genetic variation, assisted gene flow is likely to be scaled up, deliberately accelerating adaptive turnover (Prober et al., 2015).
This synthesis recasts Banksia from a static Gondwanan relic into a dynamic lineage mid-stride on an evolutionary treadmill. I now expect mid-century landscapes to host fewer, more drought-hardened species whose populations are genetic mosaics stitched together by fire, climate-driven range shifts and human seed movements—quite different from the tight local endemics pictured in older floras.
Action priorities
Climate-smart revegetation – embed provenance mixing in all Banksia restoration and infrastructure offset projects, linked to long-term common-garden trials.
Fire-interval tuning – coordinate prescribed-burn regimes so obligate seeders experience at least a 15-year respite between fires; refine with post-fire seed-bank surveys.
Genomic monitoring – use landscape-scale SNP assays every five years to track the spread of adaptive alleles and hybrid swarms across the southwest hotspot.
Ex-situ insurance – bank seed and cryopreserve tissue from range-edge and drought-sensitive taxa before projected refugia shrink further.
Implementing these steps treats evolution as an ally rather than a backdrop, boosting the odds that Banksia’s extraordinary diversity will persist—and continue to evolve—through the Anthropocene.
Reference list
Arthur Rylah Institute (2024). Fire Regimes for Banksias. [online] Victoria State Government. Available at: https://www.ari.vic.gov.au/research/emergency-events/fire/fire-regimes-for-banksias.
Cochrane, A., Hoyle, G.L., Yates, C.J., Wood, J. and Nicotra, A.B. (2014). The Phenotypic Response of co-occurring Banksia Species to Warming and Drying. Plant Ecology, 216(1), pp.27–39. doi:https://doi.org/10.1007/s11258-014-0414-z.
Fitzpatrick, M.C., Gove, A.D., Sanders, N.J. and Dunn, R.R. (2008). Climate change, Plant migration, and Range Collapse in a Global Biodiversity hotspot: the Banksia (Proteaceae) of Western Australia. Global Change Biology, 14(6), pp.1337–1352. doi:https://doi.org/10.1111/j.1365-2486.2008.01559.x.
Lamont, B.B., He, T., Enright, N.J., Krauss, S.L. and Miller, B.P. (2003). Anthropogenic Disturbance Promotes Hybridization between Banksia Species by Altering Their Biology. Journal of Evolutionary Biology, 16(4), pp.551–557. doi:https://doi.org/10.1046/j.1420-9101.2003.00548.x.
Prober, S.M., Byrne, M., McLean, E.H., Steane, D.A., Potts, B.M., Vaillancourt, R.E. and Stock, W.D. (2015). Climate-adjusted provenancing: a Strategy for climate-resilient Ecological Restoration. Frontiers in Ecology and Evolution, 3. doi:https://doi.org/10.3389/fevo.2015.00065.