Seed‐Based Rehabilitation of <i>Phytophthora cinnamomi</i> ‐Infested Forest Sites

The plant pathogen <i>Phytophthora cinnamomi</i> has significantly damaged the floristic diversity and community structure of the jarrah (<i>Eucalyptus marginata</i>) forest in Western Australia. Complete eradication of the pathogen from infested sites is not possible. This study assessed the feasibility of rehabilitating <i>P. cinnamomi</i>-infested forest sites with native resistant species using various methods of seed deployment. Precision burial of seeds at 5 mm was used as a control, mimicking optimum recruitment depths for many native species and compared against the use of extruded pellets (hereafter 'pellets') as an alternative method of precision seed placement. Eighteen rehabilitation plots were set up in three <i>P. cinnamomi</i>-infested reserves using six species. For <i>Acacia acuminata</i>, <i>A. saligna</i>, <i>Calothamnus sanguineus</i> and <i>Melaleuca seriata</i>, there were three treatments: precision buried (non-pelleted) seeds, pellets and pellets with an additive (i.e., a rhizobium bacterium for the <i>Acacia</i> spp. and ectomycorrhizal fungus spores for <i>C. sanguineus</i> and <i>M. seriata</i>). <i>Banksia sessilis</i> and <i>Hakea laurina</i> had only two treatments: precision buried (non-pelleted) seeds and pellets. Seedlings of all six species emerged successfully in <i>P. cinnamomi</i>-infested sites, and the numbers ranged between 23% and 88%. The survival of emerged seedlings after 9 months ranged between 16% and 84%, except <i>M. seriata</i>, which emerged at 59% but failed to survive. In most species, except <i>A. acuminata</i>, seedling emergence and survival from pellets were similar and within an acceptable seedling establishment range when compared to non-pelleted seeds. Pelletised seed with the addition of beneficial microbes did not improve seedling survival or shoot growth in the diseased areas of the jarrah forest. Overall, the results suggest that seedlings of resistant native species can successfully establish in <i>P. cinnamomi</i>-infested sites and pelletised seeds can be used as a viable method for precision planting.

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Publication Details

Journal
Ecology and Evolution
Published
2025-02-01
DOI
https://doi.org/10.1002/ece3.70900
Citations
2
Primary Topic
Plant Pathogens and Resistance
Type
article
Field-Weighted Citation Impact
3.50

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article

Seed‐Based Rehabilitation of Phytophthora cinnamomi ‐Infested Forest Sites

Himbutugoda S. Harshani, Treena I. Burgess, J. McComb, G.E.St.J. Hardy et al.
2 citations
Ecology and Evolution
Plant Pathogens and Resistance
3.50
article

Seed‐Based Rehabilitation of Phytophthora cinnamomi ‐Infested Forest Sites

Himbutugoda S. Harshani, Treena I. Burgess, J. McComb, G.E.St.J. Hardy, Todd E. Erickson
article en
2 citations

Abstract

The plant pathogen <i>Phytophthora cinnamomi</i> has significantly damaged the floristic diversity and community structure of the jarrah (<i>Eucalyptus marginata</i>) forest in Western Australia. Complete eradication of the pathogen from infested sites is not possible. This study assessed the feasibility of rehabilitating <i>P. cinnamomi</i>-infested forest sites with native resistant species using various methods of seed deployment. Precision burial of seeds at 5 mm was used as a control, mimicking optimum recruitment depths for many native species and compared against the use of extruded pellets (hereafter 'pellets') as an alternative method of precision seed placement. Eighteen rehabilitation plots were set up in three <i>P. cinnamomi</i>-infested reserves using six species. For <i>Acacia acuminata</i>, <i>A. saligna</i>, <i>Calothamnus sanguineus</i> and <i>Melaleuca seriata</i>, there were three treatments: precision buried (non-pelleted) seeds, pellets and pellets with an additive (i.e., a rhizobium bacterium for the <i>Acacia</i> spp. and ectomycorrhizal fungus spores for <i>C. sanguineus</i> and <i>M. seriata</i>). <i>Banksia sessilis</i> and <i>Hakea laurina</i> had only two treatments: precision buried (non-pelleted) seeds and pellets. Seedlings of all six species emerged successfully in <i>P. cinnamomi</i>-infested sites, and the numbers ranged between 23% and 88%. The survival of emerged seedlings after 9 months ranged between 16% and 84%, except <i>M. seriata</i>, which emerged at 59% but failed to survive. In most species, except <i>A. acuminata</i>, seedling emergence and survival from pellets were similar and within an acceptable seedling establishment range when compared to non-pelleted seeds. Pelletised seed with the addition of beneficial microbes did not improve seedling survival or shoot growth in the diseased areas of the jarrah forest. Overall, the results suggest that seedlings of resistant native species can successfully establish in <i>P. cinnamomi</i>-infested sites and pelletised seeds can be used as a viable method for precision planting.

Ecology and EvolutionVol. 15(2)
Murdoch University (AU), The University of Western Australia (AU)
Swan River Trust, Murdoch University, Department of Biodiversity, Conservation and Attractions
Openalex Percentile: Top 9%
Plant Pathogens and Resistance
3.50
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