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RESEARCH ARTICLE (Open Access)

Just add water: exceptional plant recruitment in arid zone mine rehabilitation

Rachel J. Standish https://orcid.org/0000-0001-8118-1904 A * , Todd E. Erickson B , Jonathan Fisher C and Tim K. Morald A
+ Author Affiliations
- Author Affiliations

A School of Environmental and Conservation Sciences and the Harry Butler Institute, Murdoch University, Murdoch, WA 6150, Australia.

B Biologic Seed Pty Ltd, East Perth, WA 6004, Australia.

C BHP Yandi, WAIO, Newman, WA 6753, Australia.

* Correspondence to: R.Standish@murdoch.edu.au

Handling Editor: Mike Calver

Pacific Conservation Biology 31, PC25024 https://doi.org/10.1071/PC25024
Submitted: 31 March 2025  Accepted: 28 April 2025  Published: 20 May 2025

© 2025 The Author(s) (or their employer(s)). Published by CSIRO Publishing. This is an open access article distributed under the Creative Commons Attribution-NonCommercial-NoDerivatives 4.0 International License (CC BY-NC-ND)

Keywords: ecological restoration, iron ore mining, low rainfall, persistent soil seed bank, Pilbara, revegetation, seed dormancy, seedling establishment.

Global extraction of precious metals has reached unprecedented levels and continues to rise with the transition from fossil fuels to renewable energy sources. Mining activity in the Pilbara region of Western Australia is among the highest in the world (Luckeneder et al. 2021). The industry is under increasing societal pressure to mitigate the environmental impacts of mining, and this includes addressing the legacies of past mining activity. Ever more, successful mine rehabilitation and closure is imperative for social licence to mine iron ore and other minerals in the region. Since 2008, BHP Western Australia Iron Ore has partnered with scientists to research improvements in rehabilitation outcomes focusing on seed biology and management in the first instance (Erickson et al. 2017).

Rehabilitation of arid-zone ecosystems is challenging; a global meta-analysis estimated that less than 10% of sown seeds establish into plants (Shackelford et al. 2021). This is due in part to complex seed dormancy mechanisms that are prevalent among arid-zone flora. In the Pilbara, at least 70% of species have dormant seeds (Erickson et al. 2017). This trait has likely evolved as a strategy to sit-and-wait for large episodic rainfall events that facilitate seedling recruitment (Erickson et al. 2017). Small-seeded species, including eucalypts, tend not to establish from direct and broadcast seeding efforts in arid regions (Shackelford et al. 2021). In the case of eucalypts, other factors including seed predation by ants and lack of a persistent soil seed bank can limit recruitment (e.g. Wellington and Noble 1985). Establishing these species may require people to plant nursery-grown seedlings despite hot temperatures and water stress that characterise rehabilitation sites. The one available field study suggests planted seedlings will establish if water is available to them (T. Erickson, unpubl. data).

Here we report the successful establishment of native vegetation following rehabilitation and irrigation to simulate summer pulse-rainfall events of a former mine overburden and iron ore storage facility (Fig. 1). The observations are remarkable for two reasons. One, woody species have successfully established from nursery-grown planted seedlings, which is rarely documented for Pilbara mine rehabilitation. In January 2024, we planted 102 Eucalyptus leucophloia Brooker (snappy gum) seedlings, irrigated them to simulate pulse-rainfall events typical of the Yandi region (Bureau of Meteorology 2023). Nineteen events totalling 352 mm, and ranging from 2 mm to 38 mm, were delivered between 1 day and up to 17 days apart between 1 February and 30 May 2024. Two months later, 34 seedlings (33%) had survived and 8 months later, 25 seedlings (25%) had established.

Fig. 1.

Vegetation 1 year after rehabilitation at Yandi in the Pilbara region of Western Australia, including planted snappy gum, sown* and, volunteer species (Table 1). *Acacia ancistrocarpa Maiden & Blakely, A. inaequilatera Domin, Triodia pungens R.Br., T. wiseana C.A.Gardner were hand sown, and T.vanleeuwenii B.M.Anderson & M.D.Barrett was direct seeded. Photo: RJ Standish, Feb 2025.


PC25024_F1.gif

Second, the unassisted recruitment of a diversity of native species is promising for future rehabilitation efforts (Table 1). The site had been used as a storage facility for overburden and ore for at least 20 years prior to its rehabilitation. After removal of the overburden and ore stockpiles, the site was deep ripped, cross ripped, deep ripped again and graded. Fresh topsoil was not added because of limited availability and concern about spreading exotic invasive buffel grass (Cenchrus ciliaris L.). The irrigation, coupled with summer rain, has triggered native plant species to recruit from wind-dispersed seeds and the remnant soil seed bank on site (Fig. 1). Comparatively few weeds recruited (Table 1). The remarkable observation is not that irrigation and rainfall triggered plant recruitment, but rather that there was potential for high-diversity native plant establishment in the absence of fresh topsoil.

Table 1.Plant species that self-recruited at Yandi within the first year of rehabilitation.

SpeciesFamilySpeciesFamily
Trianthema triquetrum Willd.AizoaceaeSenna glutinosa subsp. ×luerssenii (Domin) RandellFabaceae
*Aerva javanica (Burm.f.) Schult.AmaranthaceaeSenna glutinosa subsp. pruinosa (F.Muell.) RandellFabaceae
Gomphrena cunninghamii (Moq.) DruceAmaranthaceaeSenna notabilis (F.Muell.) RandellFabaceae
Ptilotus astrolasius F.Muell.AmaranthaceaeAbutilon sp. MillMalvaceae
Ptilotus calostachyus F.Muell.AmaranthaceaeCorchorus lasiocarpus HalfordMalvaceae
Ptilotus exaltatus NeesAmaranthaceaeSida fibulifera Lindl.Malvaceae
Ptilotus gomphrenoides Benth.AmaranthaceaeEucalyptus sp. L’Hér.Myrtaceae
Cynanchum floribundum R.Br.ApocynaceaeBoerhavia coccinea Mill.Nyctaginaceae
Lepidium sp. L.BrassicaceaeBoerhavia schomburgkiana Oliv.Nyctaginaceae
Dysphania rhadinostachya (F.Muell.) A.J.Scott subsp. rhadinostachyaChenopodiaceaeAristida inaequiglumis DominPoaceae
Salsola australis R.Br.Chenopodiaceae*Cenchrus ciliaris L.Poaceae
Arivela viscosa (L.) Raf.CleomaceaeCymbopogon ambiguous (Hack.) A.CamusPoaceae
Ipomoea muelleri Benth.Convolvulaceae*Cynodon dactylon (L.) Pers.Poaceae
Euphorbia biconvexa DominEuphorbiaceaeDactyloctenium radulans (R.Br.) P.Beauv.Poaceae
*Euphorbia hirta L.EuphorbiaceaeEnneapogon caerulescens (Gaudich.) N.T.Burb.Poaceae
Acacia bivenosa DC.FabaceaeEnneapogon polyphyllus (Domin) N.T.Burb.Poaceae
Acacia colei Maslin & L.A.J.ThomsonFabaceaeEnneapogon robustissimus (Domin) N.T.Burb.Poaceae
Acacia dictyophleba F.Muell.FabaceaeEragrostis dielsii Pilg.Poaceae
Acacia pyrifolia DC.FabaceaeEriachne aristidea F.Muell.Poaceae
Alysicarpus muelleri Schindl.FabaceaePaspalidium basicladum HughesPoaceae
Indigofera linnaei AliFabaceaeSporobolus australasicus DominPoaceae
Petalostylis labicheoides R.Br.FabaceaeTriodia epactia S.W.L.JacobsPoaceae
Rhynchosia australis Benth.Fabaceae*Rumex vesicarius L.Polygonaceae
Senna artemisioides subsp. oligophylla (F.Muell.) RandellFabaceae

Exotics are marked with an asterisk. Species authorities according to the Western Australian Herbarium (1998–). Western Australian Herbarium (1998–). Florabase – the Western Australian flora. Department of Biodiversity, Conservation and Attractions. https://florabase.dbca.wa.gov.au/ (accessed 6 March 2025).

Snappy gum is characteristic of spinifex grasslands throughout the region. While irrigation is not feasible for large-scale rehabilitation, it may be warranted on smaller scales to establish snappy gum and other woody species in mine rehabilitation. The unassisted recruitment of native plant species indicates the possibility of mine rehabilitation in the absence of fresh topsoil and with rainfall to trigger seed germination and facilitate vegetation establishment.

Data availability

The data supporting the findings are included in Table 1.

Conflicts of interest

The authors declare that they have no conflicts of interest.

Declaration of funding

This research was funded by the Cooperative Research Centre for Transformations in Mining Economies as part of Project 4.6 ‘Evidence for effective climate-adapted seed-sourcing strategies’.

Acknowledgements

Thanks to Evelyn Geurts, Leah Seabourne, Emma Stock, Shane Bisby and the Banjima Land Rehabilitation Partnership for their assistance with this research. We acknowledge the Chief Investigators, Rebecca Jordan, Suzanne Prober, Martin Breed, Jake Robinson and Siegy Krauss, and Industry Partners on the larger Project 4.6.

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