Mistletoe Generates Non‐Trophic and Trait‐Mediated Indirect Interactions

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Mistletoe Generates Non‐Trophic and Trait‐Mediated Indirect Interactions Mistletoe generates non-trophic and trait-mediated indirect interactions through a shared host of herbivore consumers ALBA LAZARO-GONZALEZ , JOSE A. HODAR, AND REGINO ZAMORA Terrestrial Ecology Research Group, Department of Ecology, Faculty of Science, University of Granada, Av. Fuentenueva s/n, Granada E-18071 Spain Citation: Lazaro-Gonz alez, A., J. A. Hodar, and R. Zamora. 2019. Mistletoe generates non-trophic and trait-mediated indirect interactions through a shared host of herbivore consumers. Ecosphere 10(3):e02564. 10.1002/ecs2.2564 Abstract. Indirect interactions emerge among a wide range of herbivores sharing the same plant resource. Consumers usually belong to different trophic guilds, from folivores and sapsuckers to para- sitic plants. We propose that mistletoes parasitizing pines could play a key role acting as herbivores on host pines and coming indirectly into competition with other herbivores feeding on the same host. Changes caused by mistletoes on its host have been well studied, but its effects running across trophic webs remain unrevealed. In this study, we investigate the effect of European mistletoe (Viscum album subsp. austriacum) on the host-feeding herbivores via trait-mediated indirect interactions (TMIIs) across their shared pine host (Pinus nigra subsp. salzmannii). We performed field and laboratory experiments, and analyzed the net effect of different mistletoe parasite loads on three host-phytophagous species: the sapsucker Cinara pini (Aphididae), the winter folivore Thaumetopoea pityocampa (Thaumetopoeidae), and the summer folivore Brachyderes sp. (Curculionidae), all being members of different functional feeding groups (FFGs). We summarize the mistletoe–host–herbivore interactions by means of a TMII, where mistletoe parasitism causes non-trophic links and detrimental indirect interactions on pine-feeding herbi- vores across its shared host, suggesting a worsening of host quality as food. These indirect interactions vary according to three parameters. First, the intensity has a non-proportional relation with parasite load, showing an impact threshold on highly parasitized pines. Second, the movement capacity of insect herbivores determines their response, by decreasing the abundance of herbivores with low movement ability (aphids and pine processionary caterpillars) while altering the behavior (plant selection) of more mobile herbivores (pine weevils). Finally, FFG determines the intensity of mistletoe parasitism effects, folivores being more responsive than sapsuckers. Overall, mistletoe generates non-trophic interaction linkages in the forest able to modify community structure by becoming a nexus of the entire herbivore community of the pine canopy. Key words: aphids; folivores; hemiparasite; host pine; insect herbivores; Mediterranean forest; pine processionary; pine weevil; plant–animal interaction; sapsuckers; Viscum album. Received 3 December 2018; accepted 11 December 2018. Corresponding Editor: Debra P. C. Peters. Copyright: © 2019 The Authors. This is an open access article under the terms of the Creative Commons Attribution License, which permits use, distribution and reproduction in any medium, provided the original work is properly cited. E-mail: [email protected] INTRODUCTION be a common phenomenon, but little known (Hochberg and Lawton 1990, Wardle et al. 2004, Plants are simultaneously consumed by organ- Bass et al. 2010). In fact, studies on interactions isms as diverse such as insects, vertebrates, fungi, between invertebrate consumers of the same nematodes, or parasitic plants. The resulting plant have documented both competitive and interactions between phylogenetically disparate positive interactions (Denno et al. 1995, Ohgushi organisms sharing a common resource appear to 2005), and the consequences of the participating ❖ www.esajournals.org 1 March 2019 ❖ Volume 10(3) ❖ Article e02564 LAZARO-GONZALEZ ET AL. species for the population dynamics have been host species could affect other host consumers in examined (Denno et al. 2000, Ohgushi 2005). several ways, running across the trophic web to These consumers induce plant responses (Karban primary (herbivores) and secondary consumers and Baldwin 1997) and generate interaction link- (predators and insectivorous birds). Therefore, ages caused by non-trophic indirect effects, able mistletoe parasitism could be the starting point to modify the food-web structure (Ohgushi 2005, for a novel case of TMIIs, where the initiator of 2008). Indirect effects can result from changes in these indirect interactions is a plant, resembling the density of a species involved in a food web, an herbivore but with effects disproportionately triggering interactions known as density- strong with respect to their size (Watson 2001, mediated indirect interactions (Peacor and Wer- Hartley et al. 2015). These indirect interactions ner 1997, Werner and Peacor 2003) or, alterna- link mistletoes with host-feeding herbivores tively, changes in the phenotypes of any species mediated by changes in traits of its shared plant- (morphological, physiological, phenological, and host. behavioral) involved in a trophic web, thus caus- In this study, we aim to investigate the indirect ing the trait-mediated indirect interactions effects of the European mistletoe (Viscum album (TMIIs; Werner and Peacor 2003, Schmitz et al. subsp. austriacum) on population responses of 2004, Gomez and Gonzalez-Meg ıas 2007). herbivores, through mistletoe-induced changes Despite recent advances in the knowledge of on their shared black pine host (Pinus nigra indirect interactions, there are hardly any studies subsp. salzmannii). Using field and laboratory on the magnitude and ecological importance of manipulation experiments, we tested the hypoth- the interactions between parasitic plants as initia- esis that the presence of mistletoe would influ- tors and insects as receptors, that use the same ence a range of insect herbivores and that this plant as the intermediary, and in turn as a trophic impact would be proportional to mistletoe abun- resource (Hartley and Gange 2009; but see Bass dance. We focused the study site in a Mediter- et al. 2010 and Ewald et al. 2011). ranean mountain (Natural Park of Sierra de The direct impact of parasitic plants on their Baza) in southeastern Spain, where V. album par- hosts, unlike that of herbivores, is often dispro- asitizes mainly P. nigra. Our study system repre- portionately strong in relation to their abun- sents a particular case because, while many dance (Watson 2001, 2009, Hartley et al. 2015) plant–parasite interactions have been studied in and able to restructure the plant (Pennings and short-lived organisms (Bass et al. 2010, Ewald Callaway 1996, Davies et al. 1997, Hodar et al. et al. 2011), here we work with two long-lived 2018) and invertebrate community (Stevens and plants (>300 yr for P. nigra, until 40 yr for mistle- Hawksworth 1970, Hartley et al. 2015). Parasitic toe). Furthermore, pines parasitized by mistletoe plants are also the trigger for a series of indirect show a high rate of re-infestation (Mellado and interactions with many other species in the com- Zamora 2016), which increases the host parasite munity located at different trophic levels. Para- load, leading eventually to death (Mellado and sitic plants can compete with other species that Zamora 2016). Thus, while herbivory is generally consume the host plant, such as herbivores, episodic, increasing in intensity over short time which represent a potentially limiting shared periods (outbreaks of defoliators), mistletoe con- resource (Gomez 1994, Puustinen and Mutikai- stitutes a chronic, long-term stressor, sequester- nen 2001). Additionally, as parasitic plants can ing water and macronutrients continuously from change the morphology and architecture of their the host (Schulze et al. 1984, Ehleringer et al. host, they can also affect other species that use 1985). In a previous study, we show how the pine the host as a habitat (Mooney et al. 2006). This is host responds to different mistletoe parasite the case of mistletoes, hemiparasitic plants able loads by altering the chemical profile of pine nee- to play a prominent role in the forest canopy act- dles, decreasing their quality as food, and syn- ing as an herbivore (Ehleringer et al. 1985, Pen- thesizing defense compounds in moderate and nings and Callaway 2002, Zuber 2004), taking highly parasitized pines (Lazaro-Gonz alez et al. up minerals and nutrients through the hausto- 2019). Thus, from the standpoint of a pine-eating rium embedded in the host xylem (Kuijt 1977, arthropod, there are three potential food sources: Zuber 2004). All mistletoe-induced changes on unparasitized pines, parasitized pines, and the ❖ www.esajournals.org 2 March 2019 ❖ Volume 10(3) ❖ Article e02564 LAZARO-GONZALEZ ET AL. mistletoe itself. We know now that the last possi- MATERIALS AND METHODS bility is not an option, because the arthropods feeding on mistletoe are narrow specialists Study site (Lazaro-Gonz alez et al. 2017). Mistletoe, Viscum album subsp. austriacum Herbivore insects are more likely to respond (Wiesb. Vollman), is a dioecious parasitic plant quickly to mistletoe parasitism in relation to native to the European region that specializes in changes in the host, due to their short life cycles parasitizing conifers, mainly Pinus species, across and sensitivity to food quality throughout the its distribution range (Zuber 2004). This study first instars (Hodar et al. 2002, Zalucki et al. was conducted in the Natural Park
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