Boom and bust: rapid feedback responses between insect outbreak dynamics and canopy leaf area impacted by rainfall and CO2

Frequency and severity of insect outbreaks in forest ecosystems are predicted to increase with climate change. How this will impact canopy leaf area in future climates is rarely tested. Here, we document function of insect outbreaks that fortuitously and rapidly occurred in an ecosystem under free‐a...

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Bibliographic Details
Published inGlobal change biology Vol. 22; no. 11; pp. 3632 - 3641
Main Authors Gherlenda, Andrew N., Esveld, Jessica L., Hall, Aidan A. G., Duursma, Remko A., Riegler, Markus
Format Journal Article
LanguageEnglish
Published Oxford Blackwell Publishing Ltd 01.11.2016
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Summary:Frequency and severity of insect outbreaks in forest ecosystems are predicted to increase with climate change. How this will impact canopy leaf area in future climates is rarely tested. Here, we document function of insect outbreaks that fortuitously and rapidly occurred in an ecosystem under free‐air CO2 enrichment. Over the first 2 years of CO2 fumigation of a naturally established mature Eucalyptus woodland, we continuously assessed population responses of three sap‐feeding insect species of the psyllid genera Cardiaspina, Glycaspis and Spondyliaspis for up to ten consecutive generations. Concurrently, we quantified changes in the canopy leaf area index (LAI). Large and rapid shifts in psyllid community composition were recorded between species with either flush (Glycaspis) or senescence‐inducing (Cardiaspina, Spondyliaspis) feeding strategies. Within the second year, two psyllid species experienced significant and rapid population build‐up resulting in two consecutive outbreaks: first, rainfall stimulated Eucalyptus leaf production increasing LAI, which supported population growth of flush‐feeding Glycaspis without impacting LAI. Glycaspis numbers then crashed and were followed by the outbreak of senescence‐feeding Cardiaspina fiscella that led to significant defoliation and reduction in LAI. For all three psyllid species, the abundance of lerps, protective coverings excreted by the sessile nymphs, decreased at e[CO2]. Higher lerp weight at e[CO2] for Glycaspis but not the other psyllid species provided evidence for compensatory feeding by the flush feeder but not the two senescence feeders. Our study demonstrates that rainfall drives leaf phenology, facilitating the rapid boom‐and‐bust succession of psyllid species, eventually leading to significant defoliation due to the second but not the first outbreaking psyllid species. In contrast, e[CO2] may impact psyllid abundance and feeding behaviour, with psyllid species‐specific outcomes for defoliation severity, nutrient transfer and trophic cascades. Psyllid populations feeding on Eucalyptus experience rapid boom‐and‐bust cycles depending on availability of suitable foliage driven by rainfall patterns and leaf phenology.
Bibliography:Figure S1. Lerps excreted by three psyllids species and leaf damage by Cardiaspina fiscella on Eucalyptus tereticornis at the Eucalyptus free-air CO2 enrichment (EucFACE) site. Figure S2. Mean monthly leaf litter fall at Eucalyptus free-air CO2 enrichment (EucFACE) site. Figure S3. Total monthly rainfall occurring at the Eucalyptus free-air CO2 enrichment (EucFACE) site. Figure S4. Mean monthly number of Glycaspis sp. lerps collected from the woodland floor and dLAI values from the previous month at the Eucalyptus free-air CO2 enrichment (EucFACE) site. Figure S5. Mean monthly number of Cardiaspina fiscella lerps collected from the woodland floor and dLAI values at the Eucalyptus free-air CO2 enrichment (EucFACE) site. Figure S6. Mean monthly number of Spondyliaspis sp. lerps collected from the woodland floor and dLAI values at the Eucalyptus free-air CO2 enrichment (EucFACE) site. Figure S7. Psyllid lerp abundance against dLAI values. Figure S8. Mean dry weight of individual lerps from three psyllid species collected at the EucFACE experimental site under ambient and elevated CO2 treatments during the peak abundance for each respective species. Table S1. Reference specimens for the three psyllid species for which lerp abundance was assessed at the EucFACE site. Table S2. Model output of the relationship between psyllid species and dLAI reanalysed with outliers removed. Table S3. Weight of dry psyllid lerps (kg ha−1) falling to the woodland floor under ambient and elevated CO2 treatments during the month in which their abundance peaked at the EucFACE site.
Hawkesbury Institute for the Environment
ArticleID:GCB13334
Australian Commonwealth Government
NSW Government
Western Sydney University
ark:/67375/WNG-7GXJN638-6
istex:6BD607C55F08C90C88C23D699EAED09FEF4B3484
ObjectType-Article-1
SourceType-Scholarly Journals-1
ObjectType-Feature-2
content type line 23
ISSN:1354-1013
1365-2486
DOI:10.1111/gcb.13334