1. Ecology

Plant-associated CO2 mediates long-distance host location and foraging behaviour of a root herbivore

  1. Carla CM Arce
  2. Vanitha Theepan
  3. Bernardus CJ Schimmel
  4. Geoffrey Jaffuel
  5. Matthias Erb  Is a corresponding author
  6. Ricardo AR Machado  Is a corresponding author
  1. Institute of Biology, University of Neuchâtel, Switzerland
  2. Institute of Plant Sciences, University of Bern, Switzerland
https://doi.org/10.7554/eLife.65575
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Cite this article
  1. Carla CM Arce
  2. Vanitha Theepan
  3. Bernardus CJ Schimmel
  4. Geoffrey Jaffuel
  5. Matthias Erb
  6. Ricardo AR Machado
(2021)
Plant-associated CO2 mediates long-distance host location and foraging behaviour of a root herbivore
eLife 10:e65575.
https://doi.org/10.7554/eLife.65575
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Abstract

Insect herbivores use different cues to locate host plants. The importance of CO2 in this context is not well understood. We manipulated CO2 perception in western corn rootworm (WCR) larvae through RNAi and studied how CO2 perception impacts their interaction with their host plant. The expression of a carbon dioxide receptor, DvvGr2, is specifically required for dose-dependent larval responses to CO2. Silencing CO2 perception or scrubbing plant-associated CO2 has no effect on the ability of WCR larvae to locate host plants at short distances (<9 cm), but impairs host location at greater distances. WCR larvae preferentially orient and prefer plants that grow in well-fertilized soils compared to plants that grow in nutrient-poor soils, a behaviour that has direct consequences for larval growth and depends on the ability of the larvae to perceive root-emitted CO2. This study unravels how CO2 can mediate plant–herbivore interactions by serving as a distance-dependent host location cue.

eLife digest

Living deep in the ground and surrounded by darkness, soil insects must rely on the chemicals released by plants to find the roots they feed on. Carbon dioxide, for example, is a by-product of plant respiration, which, above ground, is thought to attract moths to flowers and flies to apples; underground, however, its role is still unclear. This gaseous compound can travel through soil and potentially act as a compass for root-eating insects. Yet, it is also produced by decaying plants or animals, which are not edible. It is therefore possible that insects use this signal as a long-range cue to orient themselves, but then switch to another chemical when closer to their target to narrow in on an actual food source.

To test this idea, Arce et al. investigated whether carbon dioxide guides the larvae of Western corn rootworm to maize roots. First, the rootworm genes responsible for sensing carbon dioxide were identified and switched off, making the larvae unable to detect this gas. When the genetically engineered rootworms were further than 9cm from maize roots, they were less able to locate that food source; closer to the roots, however, the insects could orient themselves towards the plant. This suggests that the insects use carbon dioxide at long distances but rely on another chemicals to narrow down their search at close range.

To confirm this finding, Arce et al. tried absorbing the carbon dioxide using soda lime, leading to similar effects: carbon dioxide sensitive insects stopped detecting the roots at long but not short distances. Additional experiments then revealed that the compound could help insects find the best roots to feed on. Indeed, eating plants that grow on rich terrain – for instance, fertilized soils – helps insects to grow bigger and faster. These roots also release more carbon dioxide, in turn attracting rootworms more frequently.

In the United States and Eastern Europe, Western corn rootworms inflict major damage to crops, highlighting the need to understand and manage the link between fertilization regimes, carbon dioxide release and how these pests find their food.

Introduction

Insect herbivores can use different cues to locate suitable host plants from a distance. Volatile cues, in particular, can convey information about the identity and physiological status of a host plant and are integrated by herbivores to locate host plants for oviposition and feeding (Visser and Avé, 1978). Over the years, many attractive and repellent plant volatiles were identified (Bruce et al., 2005; Späthe et al., 2013; Webster and Cardé, 2017), and the importance of individual compounds and volatile blends was documented using synthetic chemicals (Bruce and Pickett, 2011; Carrasco et al., 2015; Fraenkel, 1959; Dorn et al., 2003; Visser and Avé, 1978). More recently, molecular manipulative approaches were used to manipulate plant volatile production and herbivore perception in vivo (Fandino et al., 2019; Halitschke et al., 2008; Robert et al., 2013), thus confirming the important role of plant volatiles in plant–herbivore interactions.

While the role of plant volatiles such as green-leaf volatiles, aromatic compounds, and terpenes is well understood, much less is known about the role of plant-associated carbon dioxide (CO2) in plant–herbivore interactions. As many plant organs and their associated microbial communities release CO2, it may be integrated into herbivore foraging as a marker of metabolic activity. Datura wrightii flowers, for instance, emit the highest levels of CO2 during times of high nectar availability; as hawkmoth pollinators are attracted to CO2, they may thus use this cue to locate rewarding flowers (Goyret et al., 2008; Guerenstein et al., 2004; Guerenstein and Hildebrand, 2008; Stange, 1996; Stange, 1999; Stange and Stowe, 1999; Thom et al., 2004). Similarly, lesions in apples result in high CO2 release and attract Bactrocera tryoni fruit flies. As CO2 at corresponding concentrations is attractive to the flies, it has been suggested that they may use plant-associated CO2 to locate suitable oviposition sites (Stange, 1999).

Root-feeding insects are highly attracted to CO2 in vitro (Bernklau and Bjostad, 1998a; Bernklau and Bjostad, 1998b; Eilers et al., 2012; Hibbard and Bjostad, 1988; Jones and Coaker, 1978; Klingler, 1966; Nicolas and Sillans, 1989; Rogers et al., 2013; Strnad et al., 1986; Strnad and Dunn, 1990). Given that CO2 is produced and released by plant roots and diffuses relatively well through the soil, a likely explanation for this phenomenon is that root herbivores use CO2 as a host location cue (Bernklau and Bjostad, 1998a; Bernklau and Bjostad, 1998b; Doane et al., 1975; Erb et al., 2013; Johnson and Gregory, 2006; Johnson and Nielsen, 2012), However, the reliability of CO2 as a host location cue for root feeders has been questioned due to a number of reasons: (i) CO2 can be emitted by many other sources apart from host plant roots, including decaying organic matter, microorganisms, and non-host plants; (ii) there is a strong diurnal fluctuation in plant CO2 emissions that does not necessarily match with insect foraging habits; and (iii) other plant-released chemicals can be used by root herbivores for host location within a CO2 background (Agus et al., 2010; Eilers et al., 2012; Erb et al., 2013; Hansen, 1977; Hibbard and Bjostad, 1988; Hiltpold and Turlings, 2012; Johnson and Nielsen, 2012; Reinecke et al., 2008; Weissteiner et al., 2012). A model that may reconcile these different views is that CO2 may be used as an initial cue at long distances, while other, more host-specific volatiles may be used at shorter distances (Erb et al., 2013; Johnson et al., 2006; Johnson and Nielsen, 2012). So far, this model has not been experimentally validated, and the precise role of plant-associated CO2 as a host location cue by herbivores, in general, and root herbivores, in particular, remains unclear (Eilers et al., 2016). To the best of our knowledge, no studies so far have investigated the role of plant-associated CO2 in plant–herbivore interactions in vivo using molecular manipulative approaches.

The larvae of Diabrotica virgifera virgifera (the western corn rootworm [WCR]) feed almost exclusively on maize roots in agricultural settings and cause major yield losses in the US and Eastern Europe (Ciosi et al., 2008; Gray et al., 2009; Meinke et al., 2009; Toepfer et al., 2015). The larvae rely on a number of volatile and non-volatile chemicals to identify and locate host plants, and distinguish between suitable and less-suitable maize plants and forage within the maize root system (Hiltpold et al., 2013; Johnson and Gregory, 2006; Johnson and Nielsen, 2012; Robert et al., 2012c; Schumann et al., 2018). Non-volatile primary metabolites such as sugars and fatty acids as well as secondary metabolites such as benzoxazinoids and phenolic acid conjugates modulate larval behaviour (Bernklau et al., 2011; Bernklau et al., 2015; Bernklau et al., 2016a; Bernklau et al., 2018; Erb et al., 2015; Hu et al., 2018; Huang et al., 2017; Machado et al., 2021; Robert et al., 2012c). Volatiles including (E)-β-caryophyllene, ethylene, and CO2 attract the larvae (Bernklau and Bjostad, 1998a; Bernklau and Bjostad, 1998b; Robert et al., 2012b; Robert et al., 2012a), while methyl anthranilate repels them (Bernklau et al., 2016b). Based on the finding that high CO2 levels can outweigh the attractive effects of other maize volatiles, it was suggested that CO2 may be the only relevant volatile attractant for WCR larvae (Bernklau and Bjostad, 1998b). However, under conditions where CO2 levels are similar, WCR larvae reliably choose between host plants of different suitability using other volatile cues (Huang et al., 2017; Lu et al., 2016; Robert et al., 2012b; Robert et al., 2012a). The demonstrated ability of WCR larvae to respond to different volatile cues and the recent identification of putative CO2 receptors from transcriptomic data (Rodrigues et al., 2016) make this species a suitable model system to investigate the role of CO2 in plant–herbivore interactions. Ongoing efforts to use CO2 as a bait to control WCR in the field (Bernklau et al., 2004; Schumann et al., 2014a; Schumann et al., 2014b) provide further motivation to assess the importance of this volatile for WCR foraging.

To understand the importance of CO2 for WCR foraging in the soil, we manipulated the insect’s capacity to perceive CO2. We reduced the expression levels of three putative WCR CO2 receptor-encoding genes through RNA interference (RNAi), resulting in the identification of DvvGr2 as an essential gene for CO2 perception. Using DvvGr2-silenced larvae in combination with CO2 removal, we then assessed the importance of CO2 perception for WCR behaviour and foraging in olfactometers and soil arenas. Our experiments reveal how root-associated CO2 modulates the interaction between maize and its economically most damaging root pest and expand the current repertoire of potential adaptive explanations for the attraction of insect herbivores to CO2.

Results

Plants create CO2 gradients in the soil

Plant-emitted CO2 may be used as a host location cue by root herbivores. To understand whether the presence of plant roots is associated with higher CO2 levels, we measured CO2 levels in the soil at different distances from young maize seedlings. We observed a significant CO2 gradient in the soil, with concentrations of 548–554 ppm in the rhizosphere, 506–515 ppm at distances between 8 and 16 cm from the plant, and 460–484 ppm at distances between 16 and 32 cm (Figure 1A). At distances of more than 40 cm, CO2 levels levelled off at 425–439 ppm. We then removed the plants and remeasured CO2 levels 1 hr afterwards. In the absence of the plants, no CO2 gradient was observed, and CO2 concentrations in the soil were around 430 ppm (Figure 1B). When surrounding soil was removed and seedling roots were washed, we observed 542 ± 6.74 ppm CO2 around the roots (n = 3). Thus, the release of CO2 from maize roots can account for the CO2 difference between soil trays with and without plants. This experiment shows that elevated CO2 levels derived from roots and probably from root-associated microorganisms are temporally and spatially associated with the presence of maize roots, and may thus be used as a host location cue by the WCR. To test this hypothesis, we identified CO2 receptors in WCR larvae, genetically impair their expression, and conducted a series of behavioural experiments as described below.

Figure 1
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Plants create CO2 gradients in the soil.

(A, B) CO2 levels were determined in soil-filled trays at different distances from young maize seedlings (A) before and (B) after removing the seedlings from the system. Arrows indicate air sampling points. Different colours indicate sampling positions within three individual trays that were assayed (n = 3). Red arrows indicate samplings points in tray 1, green arrows indicate samplings points in tray 2, and blue arrows indicate samplings points in tray 3. (C, D) Mean (± SEM) CO2 levels at different distances from the plant (C) before and (D) after removing the seedlings from the system. Different letters indicate significant differences in CO2 levels in each tray position (p < 0.05 by two-way ANOVA with Holm’s multiple-comparisons test). For details regarding the statistical results, refer to Supplementary file 1. Raw data are available in Figure 1—source data 1.

Figure 1—source data 1

Raw data for Figure 1.

https://cdn.elifesciences.org/articles/65575/elife-65575-fig1-data1-v1.xlsx

The WCR genome encodes three putative CO2 receptors

To identify genes encoding putative CO2 receptors in WCR, we used known CO2 receptor-encoding gene sequences as queries against the WCR genome (available from the National Center for Biotechnology Information [NCBI]). Three putative carbon dioxide receptor candidates, DvvGr1, DvvGr2, and DvvGr3, were identified, matching three candidate genes that were found in previous transcriptome analyses (Rodrigues et al., 2016). Phylogenetic reconstruction based on in silico-predicted protein sequences revealed orthologous relationships for the three WCR candidate receptors and the receptors of several other insects (Figure 2A). Consistent with their taxonomy, we observed close homology between the protein sequences of the CO2 receptors of WCR and the protein sequences of other coleopteran insects such as Tribolium castaneum (Figure 2A). Expression levels of DvvGr1 and DvvGr2 were found to be significantly higher in the head than in the rest of the body (thorax and abdomen) of second instar WCR larvae (Figure 2B, C). No significant difference in expression was observed for DvvGr3 (Figure 2D). Protein tertiary structure and topology models indicated that all three genes encode for 7-transmembrane domain proteins, which is consistent with their roles as receptors (Figure 2B–D).

Figure 2
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The western corn rootworm (WCR) genome contains three putative carbon dioxide (CO2) receptors.

(A) Phylogenetic relationships between putative CO2 receptors based on protein sequences of different insects. Dmel: Drosophila melanogaster; Dsim: Drosophila simulans; Dsec: Drosophila sechellia; Dyak: Drosophila yakuba; Dere: Drosophila erecta; Dana: Drosophila ananassae; Dper: Drosophila persimilis; Dpse: Drosophila pseudoobscura; Dwil: Drosophila willistoni; Dgri: Drosophila grimshawi; Dmoj: Drosophila mojavensis; Dvir: Drosophila virilis; Agam: Aedes gambiae; Aaeg: Aedes aegypti; Cqui: Culex quinquefasciatus; Bmor: Bombyx mori; Tcas: Tribolium castaneum; Dvv: Diabrotica virgifera virgifera (WCR). Evolutionary relationships were inferred using the neighbor-joining method. The optimal tree with the sum of branch length = 4.44068889 is shown. The percentage of replicate trees in which the associated taxa clustered together in the bootstrap test (100 replicates) are shown next to the branches. The tree is drawn to scale, with branch lengths in the same units as those of the evolutionary distances used to infer the phylogenetic tree. The evolutionary distances were computed using the Poisson correction method and are in the units of the number of amino acid substitutions per site. A total of 242 amino acid positions were included in the final data set. (B–D) Mean (± SEM) relative gene expression levels of group 1 (DvvGr1) (B), group 2 (DvvGr2) (C), and group 3 (DvvGr3) (D) CO2 receptors in the bodies (thorax and abdomen) or heads of second instar WCR larvae (n = 10). Asterisks indicate statistically significant differences between tissue types within genes (***p < 0.001 by Student’s t test; n.s.: not significant). For details regarding the statistical results, refer to Supplementary file 1. Raw data are available in Figure 2—source data 1. (B–D) Predicted protein tertiary structure (left) and transmembrane protein topology (right) of (B) DvvGr1; (C) DvvGr2, and (D) DvvGr3 according to the Phyre2 algorithm.

Figure 2—source data 1

Raw data for Figure 2.

https://cdn.elifesciences.org/articles/65575/elife-65575-fig2-data1-v1.xlsx

DvvGr2 expression is specifically required for responsiveness of WCR larvae to CO2

To determine the importance of DvvGr1, DvvGr2, and DvvGr3 for the responsiveness of WCR larvae to CO2, we knocked down the expression of each gene individually through double-stranded RNA (dsRNA)-mediated RNAi and conducted initial behavioural experiments with carbonated water as a CO2 source (Figure 3). Oral administration of dsRNA targeting either DvvGr1, DvvGr2, or DvvGr3 reduced the expression levels of these genes by 80%, 83%, and 66% compared to WCR larvae fed with dsRNA of the green fluorescent protein (GFP) gene (herein referred to as wild type [WT]) (Figure 3A). All RNAi constructs were confirmed to be gene specific (Figure 3A). Measurements within the olfactometers showed that CO2 levels were approximately 100 ppm higher in the arms of the L-shaped pots that contained plastic cups filled with carbonated water than in the arms of L-shaped pots that contained plastic cups filled with distilled water (Figure 3B, Figure 3—figure supplement 1). A higher proportion of WT larvae moved towards olfactometer arms with higher CO2 levels (Figure 3C). Silencing DvvGr1 or DvvGr3 expression did not alter this preference. In contrast, DvvGr2-silenced larvae did not show preference for any olfactometer arm (Figure 3C). To explore the role of DvvGr2 in different aspects of WCR behaviour, we conducted a series of additional experiments. First, we assessed the impact of silencing DvvGr2 on the capacity of WCR larvae to respond to other volatile and non-volatile host cues (Figure 3D–G). DvvGr2-silenced larvae responded similarly to the repellent volatile methyl anthranilate as WT larvae (Figure 3E). Responsiveness to non-volatile compounds such as Fe(III)(DIMBOA)3 and a blend of glucose, fructose, and sucrose was also unaltered in DvvGr2-silenced larvae (Figure 3F, G), demonstrating that knocking down DvvGr2 expression does not alter the capacity of WCR larvae to respond to other important chemical cues. Second, we assessed the contribution of DvvGr2 to CO2 responsiveness using synthetic CO2 at different concentrations (Figure 4, Figure 4—figure supplement 1). WT larvae showed characteristic dose-dependent behavioural responses to CO2. While they did not respond to 22 ppm CO2 above ambient CO2 levels, they were attracted to CO2 concentrations between 59 and 258 ppm above ambient and repelled by CO2-enriched air at 950 ppm above ambient CO2 levels and above (Figure 4). In contrast, DvvGr2-silenced larvae did not respond to CO2 enrichment at any of the tested concentrations (Figure 4). These experiments show that WCR larvae are attracted to CO2-enriched environments within the physiological range of the maize rhizosphere and that DvvGr2 silencing fully and specifically suppresses CO2 responsiveness in WCR larvae.

Figure 3 with 1 supplement see all
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The carbon dioxide group 2 receptor (DvvGr2) is specifically required for the attraction of western corn rootworm (WCR) towards CO2.

(A) Mean (± SEM) relative gene expression levels of group 1 (DvvGr1), group 2 (DvvGr2), and group 3 (DvvGr3) CO2 receptors after WCR larvae were fed with dsRNA-expressing bacteria targeting green fluorescent protein (GFP, herein referred to as WT), DvvGr1, DvvGr2, or DvvGr3 genes (n = 11–13). Different letters indicate significant differences of gene expression levels (p < 0.05 by one-way ANOVA with Holm’s multiple-comparisons test). (B) Mean (± SEM) CO2 levels in each L-shaped pot of the two-arm belowground olfactometers used to test the attractive and repellent effects of CO2 to WCR larvae (n = 4–8). Asterisk indicates significant differences in CO2 levels (*p < 0.05 by Student’s t test). For detailed data on CO2 levels, refer to Figure 3—figure supplement 1. (C) Mean (± SEM) proportion of WCR larvae observed in the olfactometer arms with higher CO2 levels (carbonated water side) or in control arms (distilled water side). Larvae were considered to have made a choice when they were found at a distance of 1 cm or less from the wire mesh (indicated by dashed green lines). Seven olfactometers with six larvae each were assayed (n = 7). (D) Petri plates used to test insect responses to methyl anthranilate, to Fe(III)(DIMBOA)3, and to sugars. (E) Mean (± SEM) proportion of WCR larvae observed on roots or on roots placed next to filter paper discs impregnated with methyl anthranilate, (F) on filter paper discs impregnated with buffer or with Fe(III)(DIMBOA)3, and (G) on filter paper discs impregnated with buffer or with a blend of glucose, fructose, and sucrose. For (E), 10 choice arenas with five larvae each were assayed (n = 10). Larvae were considered to have made a choice when they made physical contact with the roots or the filter paper discs. For (F, G), 20 choice arenas with six larvae each were assayed (n = 20). Asterisks indicate statistically significant differences in larval choices between treatments (***p < 0.001 by generalized linear model followed by False discovery rate (FDR)-corrected post hoc tests). Note that the number of replicates across experiments varied depending on the availability of insects. For details regarding the statistical results, refer to Supplementary file 1. Raw data are available in Figure 3—source data 1.

Figure 3—source data 1

Raw data for Figure 3.

https://cdn.elifesciences.org/articles/65575/elife-65575-fig3-data1-v1.xlsx
Figure 4 with 1 supplement see all
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DvvGr2 is required for dose-dependent western corn rootworm (WCR) responses to CO2.

(A) Two-arm olfactometer used to test the attractive and repellent effects of CO2 on WCR larvae. (B) Mean ( ± SEM) proportion of WCR larvae observed in each arm of the olfactometers. Larvae were considered to have made a choice when they were found at a distance of 1 cm or less from the wire mesh, indicated by dashed green lines. Three olfactometers with six larvae each were assayed (n = 3). Asterisks indicate statistically significant differences between larval choices (*p < 0.05; **p < 0.01; ***p < 0.001 by generalized linear model [GLM] followed by FDR-corrected post hoc tests). Mean CO2 concentrations in each olfactometer side and the difference between them (∆CO2) are indicated. Asterisks indicate significant differences in the CO2 levels of each olfactometer arm (*p < 0.05; **p < 0.01; *** p < 0.001 by GLM followed by FDR-corrected post hoc tests). For detailed data on CO2 levels, refer to Figure 4—figure supplement 1. For details regarding the statistical results, refer to Supplementary file 1. Raw data are available in Figure 4—source data 1.

Figure 4—source data 1

Raw data for Figure 4.

https://cdn.elifesciences.org/articles/65575/elife-65575-fig4-data1-v1.xlsx

DvvGr2 expression does not affect larval motility or short-range host location

To assess the impact of DvvGr2 on larval motility, we followed the trajectories of individual larvae in humid filter paper-lined Petri plates that were outfitted with a CO2 point releaser (Figure 5). WT larvae made frequent turns, but consistently oriented themselves towards the CO2 release point. Once they reached the CO2 release point, they stopped moving (Figure 5A). DvvGr2-silenced larvae exhibited similar turning behaviour as WT larvae, but did not move towards the CO2 release point (Figure 5B). WT larvae spend more time on CO2 release point than DvvGr2-silenced larvae (Figure 5C). During the movement phase, the mean speed of WT larvae and DvvGr2-silenced larvae was similar (Figure 5C), but the distance covered by DvvGr2-silenced larvae was higher, as they did not stop at the CO2 release point. In a second experiment, we followed the trajectories of individual larvae in Petri plates with maize roots (Figure 5D, E). Speed and distance covered were similar between WT and DvvGr2-silenced larvae (Figure 5F). Surprisingly, both WT and DvvGr2-silenced larvae oriented themselves towards the maize roots and reached the maize roots after a similar amount of time (Figure 5F). This result shows that DvvGr2 expression is required for the location and detection of CO2, but does not influence WCR motility nor its ability to locate maize roots over short distances (i.e.,<9 cm).

Figure 5
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Silencing the carbon dioxide group 2 receptor (DvvGr2) impairs western corn rootworm (WCR) responses to CO2 without affecting larval motility or search behaviour.

(A, B) Trajectories of individual wild type (WT) (A) and DvvGr2-silenced (B) WCR larvae in Petri plates with a CO2 source. The blue circles represent larval release points. The red circles represent CO2 sources consisting of a fine needle that releases CO2 at 581 ppm, resulting in CO2 concentrations 60 ppm above ambient CO2 levels at the release point. (C) Mean (± SEM) speed and distance covered during the movement phase, and time spent at the CO2 source during the first 3 min of the experiment. (D, E) Trajectories followed by WT (D) and by DvvGr2-silenced (E) WCR larvae on Petri plates containing maize seedling roots. The blue circles represent larval release points. The yellow circles represent maize seedling roots. (F) Mean (± SEM) speed and distance covered during the movement phase, and time necessary to reach the maize root during the first 3 min of the experiment. For both experiments, six Petri plates with one larva each were assayed (n = 6). Asterisks indicate statistically significant differences between mobility parameters of WT and DvvGr2-silenced larvae (***p < 0.001 by Student’s t test). For details regarding the statistical results, refer to Supplementary file 1. Raw data are available in Figure 5—source data 1.

Figure 5—source data 1

Raw data for Figure 5.

https://cdn.elifesciences.org/articles/65575/elife-65575-fig5-data1-v1.xlsx

Root-associated CO2 enhances volatile-mediated host location by WCR larvae in a distance-specific manner

To further explore the role of plant-associated CO2 and DvvGr2 in volatile-mediated host location, we performed a series of olfactometer experiments with maize plants grown in sand on one side and sand only on the other side. We tested attraction at two distances, 9 and 18 cm, from the volatile sources and the release points of the larvae (Figure 6). We also manipulated the diffusion of CO2 into the arms of a subset of olfactometers by adding a layer of CO2-absorbing soda lime into the olfactometer arms. CO2 measurements revealed that the presence of a host root system increased CO2 concentrations by approximately 100 ppm above ambient CO2 levels in the corresponding olfactometer arm (Figure 6, Figure 6—figure supplement 1). The soda lime reduced ambient CO2 concentrations in the olfactometer arms by approximately 100 ppm and equalized CO2 concentrations between arms with and without a host plant (Figure 6). The diffusion of other maize root volatiles was not affected by the soda lime (Figure 6—figure supplement 2), thus validating the CO2 scrubbing approach. Larvae did not have direct access to the plant, the plant growth medium, or the soda lime, and received no visual cues, and thus had to rely on host plant volatiles for orientation. When released at distance of 9 cm from the volatile sources, both WT and DvvGr2-silenced larvae showed a clear preference for the olfactometer arms leading to host plants (Figure 6A). This preference was still intact in olfactometers outfitted with soda lime, showing that volatiles other than CO2 are sufficient for volatile-mediated host location at a short distance. At a distance of 18 cm from the volatile sources, WT larvae showed a similarly strong preference for arms leading to host plants (Figure 6B). By contrast, DvvGr2-silenced larvae did not exhibit any preference (Figure 6B). In the presence of soda lime, neither WT nor DvvGr2-silenced larvae were attracted to arms with a host plant (Figure 6B). Taken together, these experiments provide strong support for the hypothesis that WCR larvae use plant-associated CO2 to locate host plants over distances greater than 9 cm in a DvvGr2-dependent manner.

Figure 6 with 2 supplements see all
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Plant-associated CO2 mediates host location by western corn rootworm (WCR) larvae in a distance-specific manner.

(A, B) Mean (± SEM) proportion (%) of WCR larvae observed on each side of the olfactometers. Larva were considered to have made a choice when they were found at a distance of 1 cm or less from the wire mesh, indicated by dashed green lines. Control olfactometers allowed for plant-associated CO2 to diffuse into the central glass tubes, while CO2 scrubber olfactometers were outfitted with soda lime to suppress CO2 diffusion while allowing for the diffusion of other volatiles. Mean CO2 concentrations in each olfactometer side and the difference between them (∆CO2) are given. Asterisks indicate significant differences in the CO2 levels of each olfactometer arm (***p < 0.001 by generalized linear model [GLM] followed by FDR-corrected post hoc tests). For detailed data on CO2 levels and other volatiles, refer to Figure 6—figure supplements 1 and 2. Four olfactometers with six larvae each were assayed using wild type (WT) or DvvGr2-silenced larvae (n = 4). Asterisks indicate statistically significant differences between treatments (**p < 0.01 by GLM followed by FDR-corrected post hoc tests). For details regarding the statistical results, refer to Supplementary file 1. Raw data are available in Figure 6—source data 1.

Figure 6—source data 1

Raw data for Figure 6.

https://cdn.elifesciences.org/articles/65575/elife-65575-fig6-data1-v1.xlsx

Root-associated CO2 enhances volatile-mediated host location by WCR larvae in a distance-specific manner

WCR larvae can move up to 1 m in the soil. Second and third instar larvae in particular are known to move between maize plants across rows in maize fields (Hibbard et al., 2003). To test whether DvvGr2-mediated CO2 responsiveness mediates host location over longer distances in a soil context, we planted maize plants in soil-filled plastic trays, released WCR larvae at distances of 16, 32, 48, or 64 cm from the maize plants, and evaluated larval positions after 8 hr (Figure 7). This time point was chosen based on preliminary observations showing that larvae take approximately 8 hr to cross the soil arenas. Direct access to the roots was impeded by using volatile-permeable fabrics, referred to hereby as root barriers. The CO2 emitted by maize roots formed a gradient in the soil, starting at about 506 ppm in the rhizosphere (zone 1) and 430 ppm at distances of 16–32 cm from the plant (zone 2) (Figure 7B, Figure 7—figure supplement 1). At distances of more than 32 cm from the plant, the CO2 levels were around 400 ppm and statistically indistinguishable from soil without plants or ambient air (Figure 7—figure supplement 1). To confirm that larval motility is not altered by DvvGr2 silencing in a soil context, we first released WT and DvvGr2-silenced larvae into the middle of a set of arenas without a host plant and evaluated larval positions after 8 hr. We found that the larvae dispersed equally across the arenas, without any difference between WT and DvvGr2-silenced larvae (Figure 7A). Eight hours after releasing the larvae into arenas that included host plants on one side, 53% of WT larvae that were released at 64 cm from the plant were retrieved close to the maize rhizosphere, that is, in zone 1 (Figure 7C). In contrast, only 33% of the DvvGr2-silenced larvae that were released at the same distance were recovered from the maize rhizosphere (Figure 7C). Significantly more DvvGr2-silenced larvae were recovered further away from the plants, in zones 3 and 4 (Figure 7C). The number of WT and DvvGr2-silenced WCR larvae found close to the host plant increased with decreasing release distance, as did the difference between WT and DvvGr2-silenced larvae (Figure 7C–F). At a release distance of 16 cm, only slightly more WT than DvvGr2-silenced larvae were found close to the plant roots (Figure 7F). To further confirm the role of DvvGr2 in mediating host plant location over long distances in the soil, we performed a time-course experiment where we released WT and DvvGr2-silenced larvae in zone 5 (64 cm away from the host plant) and then recorded how rapidly they reached zone 1 containing host plants (Figure 7—figure supplement 2). The capacity of the larvae to directly feed on the host roots was impeded using a volatile-permeable root barrier (Figure 7—figure supplement 2). Within 10 hr, 36% of the released WT larvae were found in zone 1, and within 32 hr, this number had increased to 90% (Figure 7—figure supplement 2). By contrast, only 24% of the released DvvGr2-silenced larvae were found in zone 1 after 10 hr, and after 32 hr, this value had only increased to 56% (Figure 7—figure supplement 2). Thus, the capacity to detect CO2 gradients contributes to successful host location by WCR larvae in a distance-specific manner in the soil. While larvae released at a distance equal to or below 32 cm from the host plant (zones 2–3) can use CO2 directly as a host location cue, larvae released at greater distances likely move randomly before reaching zones with plant-associated CO2 gradients.

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Root-associated CO2 is used by western corn rootworm (WCR) larvae for host location in a distance-specific manner.

(A) Mean (± SEM) proportion of wild type (WT) (dark green) or DvvGr2-silenced (light green) WCR larvae observed in the different tray zones 8 hr after releasing the larvae in the centre of soil-filled trays without plants. Three trays per larval type with 20 larvae each were assayed (n = 3). (B) Schematic representation (photomontage) of experimental set-up used to test distance-specific host location abilities of WCR larvae depicting mean (± SEM) CO2 levels detected in the soil gas phase of each tray zone (n = 3–4). Different letters indicate significant differences in CO2 levels (p < 0.05 by one-way ANOVA with Holm’s multiple-comparisons test). For detailed data on CO2 levels, refer to Figure 7—figure supplement 1. (C–F) Mean (± SEM) proportion of WT (dark green) or DvvGr2-silenced (light green) WCR larvae observed in the different tray zones 8 hr after releasing the larvae at distances of 64 cm (C), 48 cm (D), 32 cm (E), or 16 cm (F) from the plants. Six trays per larval type and distance combination with 20 larvae each were assayed (n = 6). Asterisks indicate statistically significant differences in the proportion of WT and DvvGr2-silenced larvae found in each tray zone (*p < 0.05; **p < 0.01 by generalized linear model followed by FDR-corrected post hoc tests). For details regarding the statistical results, refer to Supplementary file 1. Raw data are available in Figure 7—source data 1.

Figure 7—source data 1

Raw data for Figure 7.

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CO2 perception enhances the capacity of WCR larvae to locate better hosts

Plant nutritional status determines plant growth and defence, and can thus modulate plant–herbivore interactions (Wetzel et al., 2016). To test for a possible connection between plant nutritional status, host suitability, and CO2-dependent herbivore attraction, we varied the nutrient supply of maize plants and then carried out CO2 measurements, and behavioural and insect performance experiments (Figure 8). To exclude direct or soil-mediated effects of fertilization, plants were first grown under different fertilization regimes and then, prior to experiments, harvested, washed, and replanted. Higher CO2 levels were observed close to the roots of plants that were well fertilized compared to the levels that were observed close to the roots of plants that received medium (50% of optimally fertilized plants) or low (10% of optimally fertilized plants) fertilizer doses (Figure 8A, B, Figure 8—figure supplement 1A, B). As observed before, soil CO2 levels decreased with increasing distance from the plants and were lowest in the middle of the experimental trays (Figure 8A, B). In choice experiments with maize plants planted approximately 50 cm apart, which corresponds to row spacing used for high planting densities in maize cultivation, WT larvae showed a significant preference for well-fertilized over medium- or low-fertilized plants (Figure 8C, D). DvvGr2-silenced larvae did not show any preference (Figure 8C, D). In no-choice experiments, WCR larvae gained most weight on washed roots of well-fertilized maize plants than on washed roots of plants treated with medium or low doses of fertilizer (Figure 8E). Hence, intact CO2 perception allows WCR larvae to locate suitable host plants at agriculturally relevant distances, which may result in specific insect distribution patterns in heterogeneous environments.

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CO2 perception increases the location of more suitable host plants.

(A, B) Schematic representation (photomontage) of soil-filled trays used to evaluate location of differentially fertilized plants by western corn rootworm (WCR) larvae depicting mean (± SEM) CO2 levels detected in the soil gas phase of each tray zone (n = 10). Different letters indicate statistically significant differences in CO2 levels (p < 0.05 by one-way ANOVA with Holm’s multiple-comparisons test). For details regarding CO2 levels, refer to Figure 8—figure supplement 1. Mean (± SEM) proportion of WCR larvae recovered close to plants that received low (zone 5) or optimum (zone 1) fertilizer doses (C), or that were recovered close to plants that received medium (zone 5) or optimum (zone 1) fertilizer doses (D) 8 hr after releasing the larvae. Six trays with 20 larvae per tray were assayed (n = 6). Different letters indicate statistically significant differences in larval preferences (*p < 0.05; ***p < 0.001 by generalized linear model followed by FDR-corrected post hoc tests). (E) Mean (± SEM) weight of WCR larvae after 7 days feeding on plants fertilized with low, medium, or optimum fertilizer doses. Twenty solo cups with 4–7 larvae each were assayed (n = 20). Different letters indicate statistically significant differences in larval mass (p < 0.05 by one-way ANOVA followed by Holm’s multiple-comparisons tests). For details regarding the statistical results, refer to Supplementary file 1. Raw data are available in Figure 8—source data 1.

Figure 8—source data 1

Raw data for Figure 8.

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Discussion

In this study, we conducted gene sequence similarity analyses, phylogenetic relationship reconstructions, RNA interference, and behavioural experiments to explore the biological relevance of root-associated CO2 for plant–herbivore interactions. We found that the WCR genome contains at least three putative CO2 receptor-encoding genes: DvvGr1, DvvGr2, and DvvGr3, which is consistent with previous transcriptomic-based studies (Rodrigues et al., 2016). Protein tertiary structure and topology prediction models show that the identified genes code for proteins that contain seven transmembrane domains, which is consistent with the protein topology of gustatory and olfactory receptors (Dahanukar et al., 2005; Hallem et al., 2006). Larval behaviour and gene silencing based-functional characterization of the three identified WCR putative CO2 receptor genes revealed that the intact expression of DvvGr2 is essential for the attractive effects of CO2 to WCR larvae. Knocking down DvvGr2 rendered larvae fully unresponsive to synthetic and plant-associated CO2 without impairing responses to other stimuli or affecting search behaviour and motility. In Aedes aegypti, Helicoverpa armigera, and Drosophila melanogaster, both carbon dioxide receptors Gr1 and Gr3 are required for CO2 detection (Erdelyan et al., 2012; Jones et al., 2007; Kwon et al., 2007; McMeniman et al., 2014; Ning et al., 2016; Suh et al., 2004). In Culex quinquefasciatus, both Gr2 and Gr3 carbon dioxide receptors are required, while Gr1 acts as a modulator (Xu et al., 2020). In A. aegypti, the involvement of Gr2 in carbon dioxide responsiveness is still under debate (Erdelyan et al., 2012; Kumar et al., 2019). Taken together, the molecular elements required for carbon dioxide perception may be species-specific. Our results support this notion as DvvGr2, but not DvvGr1 and DvvGr3, are crucial for CO2 responsiveness. The role of DvvGr1 and DvvGr3 for WCR remains to be determined, but their presence and expression may hint at additional complexity in developmental and/or tissue-specific patterns of CO2 responsiveness in this species.

Despite the inability of DvvGr2-silenced WCR larvae to respond to differences in CO2 levels, the larvae were still able to orient towards maize roots at short distances of 8–10 cm. Olfactometer experiments in combination with CO2 removal demonstrate that other volatile cues can be used by WCR larvae to locate maize plants at distances shorter than 9 cm. Earlier studies found that (E)-β-caryophyllene, which is emitted from the roots of certain maize genotypes when they are attacked by root herbivores, attracts second and third instar WCR larvae and allows them to aggregate on maize plants and thereby enhance their fitness (Robert et al., 2012b), while neonate larvae are not attracted to this volatile (Hiltpold and Hibbard, 2016). Ethylene has also been shown to attract WCR larvae (Robert et al., 2012a), and MBOA or its breakdown products have also been proposed as volatile attractants (Bjostad and Hibbard, 1992). Methyl anthranilate, on the other hand, has been shown to repel WCR larvae (Bernklau et al., 2016b; Bernklau et al., 2019). Many other leaf- and root-feeding herbivores are known to respond to plant volatiles other than CO2 (Bruce et al., 2005). Given the low reliability of CO2 as a host-specific cue, it is probably not surprising that WCR, as a highly specialized maize feeder, can use other volatile cues to locate host plants. Integrating other volatile cues likely allows WCR larvae to locate maize plants even in the absence of reliable CO2 gradients in the soil, thus increasing the robustness of its foraging behaviour at short distances. An intriguing result in this context is the fact that WCR larvae show the same efficiency in locating maize roots at short distances in the absence of a CO2 gradient, suggesting that this volatile may not play a role as a cue at close range.

Although intact CO2 perception was not required for host location at short distances, it had a strong impact on the capacity of WCR larvae to reach the maize rhizosphere at long distances. A gradient of plant-associated CO2 was detected at distances of up to 32 cm from the plant. When WCR larvae were released at distances greater than 32 cm, they still managed to locate plants in a DvvGr2-dependent manner. This result can be explained by random movement, where the larvae move randomly until they encounter a CO2 gradient, or by localized CO2 gradients along preferential gas-phase pathways that may extend beyond 32 cm, or a combination of both. The advantages of CO2 as a host location cue are that it is abundantly produced through respiration by most organisms, is relatively stable (Jones and Coaker, 1977; Li et al., 2016), and diffuses rapidly in air, water, and soil (Hashimoto and Suzuki, 2002; Ma et al., 2013). CO2 may thus be a suitable long-range cue to locate organisms with high respiratory rates, such as mammals and heterotroph plant parts, including roots and their associated microbial communities (Johnson and Nielsen, 2012). Aboveground insects can be attracted to CO2 traps located as far away as 10 m, and it is estimated that this distance could even be as long as 60 m under optimal environmental circumstances (Guerenstein and Hildebrand, 2008; Zollner et al., 2004). For belowground insects, this distance is hypothesized to be within the lower centimetre range as CO2 diffusion is substantially decreased within the soil matrix compared to CO2 diffusion in air (Bernklau et al., 2005; Doane et al., 1975; Doane and Klingler, 1978; Klingler, 1966). Other volatiles that are less abundant and diffuse even less well through the soil such as (E)-β-caryophyllene are unlikely to be detectable at distances of more than 10 cm (Chiriboga M. et al., 2017; Hiltpold and Turlings, 2008). These volatiles are thus likely useful host location cues at short, but not long, distances in the soil. The finding that WCR integrates CO2 perception with other environmental cues and that attraction to CO2 is context dependent is in line with patterns reported for other insects such as mosquitoes, whose response to stimuli such as colour, temperature, and human body odours is enhanced by CO2 (McMeniman et al., 2014; van Breugel et al., 2015), and pollinating hawkmoths, which use CO2 as a redundant volatile distance stimulus in a sex-specific manner (Goyret et al., 2008).

A recent study shows that a CO2 receptor in Drosophila flies is also involved in the detection and behavioural responses to other volatiles (MacWilliam et al., 2018). We observed that DvvGr2-silenced larvae were repelled by methyl anthranilate, a potent maize root repellent, to a similar extent as WT larvae, suggesting that their sensitivity to this plant volatile is unchanged (Bernklau et al., 2016b). In Drosophila flies, the CO2 receptor Gr63a is required for spermidine attractiveness over short time spans, that is, less than 1 min, but not over longer time spans (hours), when other receptors likely become more important (MacWilliam et al., 2018). In the present experiments, WCR behaviour was evaluated after one or more hours. The CO2 scrubber experiment provides further evidence that the foraging patterns observed in this study are not due to different sensitivity of DvvGr2-silenced larvae to other root volatiles.

Apart from acting as a long-distance host location cue, CO2 also links plant fertilization to herbivore behaviour by guiding WCR to well-fertilized plants. As WCR larvae are resistant to root defences of maize (Robert et al., 2012b), it is likely to benefit from increased fertilization, independently of the plant’s defensive status. As the plant nutritional status and host quality for WCR larvae are associated with higher CO2 release from the roots, following the highest concentrations of CO2 in the soil may be adaptive for the herbivore as it may increase its chance not only to find a maize plant per se but also to identify a plant that has the resources to grow vigorously and that is a better host. More experiments are needed to confirm this hypothesis as in the current set-up the larvae may have followed the only available CO2 gradient close to their release point rather than having made a choice between two gradients. However, given the dose-dependent responses of WCR, preferential orientation towards plants surrounded by higher CO2 levels appears likely. Well-fertilized maize plants increase photosynthesis and biomass production, which results in higher CO2 release from the roots (Zhu and Lynch, 2004). WCR larvae are specialized maize pests that have evolved with intense maize cultivation in the corn belt of the US (Gray et al., 2009) and are resistant to maize defence metabolites (Robert et al., 2012b). Following the strongest CO2 gradient in an equally spaced maize monoculture may indeed be a useful strategy for this root feeder to locate suitable food sources. An association between CO2 emission and food-source profitability was also suggested for Datura flowers, which emit the highest level of CO2 in times when nectar is most abundant (Guerenstein et al., 2004; Thom et al., 2004). These findings support the general hypothesis that CO2 is a marker of metabolic activity that allows for an assessment of the vigour and profitability of a wide variety of hosts. The impact of CO2 for the distribution of root herbivores such as the WCR in heterogeneous environments remains to be determined. Based on our results, we expect plant-associated CO2 to contribute to uneven herbivore distribution and to aggregation on plants with a good nutritional status within monocultures.

In summary, this work demonstrates how a herbivore uses its capacity to perceive CO2 to locate host plants. Volatiles other than CO2 are also integrated into host-finding behaviour in the soil, but their effects are more important at short than at long distances. Random movement in the soil may help this root herbivore to increase its capacity to find host cues at even greater distances. Thus, evidence is now accumulating that CO2 acts as an important host location cue in different insects, likely because of its unique role as a highly conserved long-range marker of metabolic activity within complex sensory landscapes.

Materials and methods

Plants and planting conditions

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Maize seeds (Zea mays L., var. Akku) were provided by Delley Semences et Plantes SA (Delley, Switzerland). Seedlings were grown under greenhouse conditions (23 ± 2°C, 60% relative humidity, 16:8 h L/D, and 250 mmol/m2/s1 additional light supplied by sodium lamps). Plantaaktiv 16+6+26 Typ K fertilizer (Hauert HBG Dünger AG, Grossaffoltern, Switzerland) was added twice a week after plant emergence following the manufacturer’s recommendations. The composition of the fertilizer is: total nitrogen (N) 16%, nitrate 11%, ammonium 5%, phosphate (P2O5) 6%, potassium oxide (K2O) 26%, magnesium oxide (MgO) 3.3%, boron (B) 0.02%, copper (Cu, EDTA-chelated) 0.04%, iron (Fe, EDTA-chelated) 0.1%, manganese (Mn, EDTA-chelated) 0.05%, molybdenum (Mo) 0.01%, and zinc (Zn, EDTA-chelated) 0.01%. When plants were used as insect food, seedlings were germinated in vermiculite (particle size: 2–4 mm; tabaksamen, Switzerland) and used within 4 days after germination.

Insects and insect rearing

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Diabrotica virgifera virgifera (WCR) insects used in this study were derived from a non-diapausing colony reared at the University of Neuchâtel. The eggs used to establish the colony were supplied by USDA-ARS-NCARL, Brookings, SD. New insects of the same origin are introduced into the colony every 3–6 months. Upon hatching, insects were maintained in organic soil (Selmaterra, Bigler Samen AG, Thun, Switzerland) and fed freshly germinated maize seedlings (var. Akku).

Identification of CO2 receptor genes

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To identify CO2 receptor orthologues in WCR, we used CO2 receptor-encoding gene sequences of T. castaneum and several sequences from other insects as queries against publicly available WCR genome sequences (NCBI accession: PXJM00000000.2) using the National Center for Biotechnology Information Basic Local Alignment Search Tool (NCBI BLAST) (Robertson and Kent, 2009; Wang et al., 2013; Xu and Anderson, 2015). The full gene sequences can be retrieved from the NCBI databank using the following accession numbers: XM_028276483.1 (DvvGr1), XM_028280521.1 (DvvGr2), and XM_028272033.1 (DvvGr3). These gene sequences were translated to obtain protein sequences. The obtained protein sequences and the protein sequences of CO2 receptors from different insects were used to infer evolutionary relationships using the neighbor-joining method in MEGA 7 (Kumar et al., 2016; Robertson and Kent, 2009; Rodrigues et al., 2016; Saitou and Nei, 1987). The optimal tree with the sum of branch length = 4.44068889 is provided in Figure 2A. The percentage of replicate trees in which the associated taxa clustered together in the bootstrap test (100 replicates) are shown next to the branches (Felsenstein, 1985). The tree is drawn to scale, with branch lengths in the same units as those of the evolutionary distances used to infer the phylogenetic tree. The evolutionary distances were computed using the Poisson correction method (Zuckerkandl and Pauling, 1965) and are in the units of the number of amino acid substitutions per site. A total of 242 amino acid positions were included in the final data set. Graphical representation and edition of the phylogenetic tree were performed with the Interactive Tree of Life (version 3.5.1) (Letunic and Bork, 2016). Protein tertiary structures and topologies were predicted using Phyre2 (Kelley et al., 2015).

Production of dsRNA

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Escherichia coli HT115 were transformed with recombinant L4440 plasmids that contained a 211–240 bp long gene fragment targeting one of the three CO2 receptors. Cloned nucleotide sequences were synthetized de novo (Eurofins, Germany). To induce the production of dsRNA, an overnight bacterial culture was used to inoculate fresh Luria–Berthani broth (25 g/L, Luria/Miller, Carl Roth GmbH, Karlsruhe, Germany). Once the bacterial culture reached an OD600 of 0.6–0.8, it was supplemented with isopropyl β-D-1-thiogalactopyranoside (Sigma-Aldrich, Switzerland) at a final concentration of 2 mM. Bacterial cultures were incubated at 37°C in an orbital shaker (Ecotron, Infors HT, Bottmingen, Switzerland) at 130 rpm for 16 additional hours. Bacteria were harvested by centrifugation (2000 rpm, 10 min) using a top bench centrifuge (IEC Centra GP6R, Thermo Fisher Scientific, Waltham, MA, USA) and stored at −20°C in a freezer (Bosch, Gerlingen, Germany) for further use (Kim et al., 2015).

Gene silencing experiments

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To induce gene silencing in WCR, 6–10 second instar WCR larvae were released in solo cups (30 ml, Frontier Scientific Services, Inc, Germany) containing approximately 2 g of autoclaved soil (Selmaterra, Bigler Samen AG, Thun, Switzerland) and 2–3 freshly germinated maize seedlings. Maize seedlings were coated with 1 ml of bacterial solution containing approximately 200–500 ng of dsRNA targeting the different CO2 receptor genes. As controls, larvae were fed with bacteria-producing dsRNA-targeting GFP genes, which are absent in the WCR genome (Rodrigues et al., 2016). dsRNA was produced as described above. Fresh bacteria and seedlings were added to solo cups every other day for three consecutive times. Two days after the last dsRNA/bacteria application, larvae were collected and used for experiments.

Gene expression measurements

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Total RNA was isolated from approximately 10 mg of frozen, ground, and homogenized WCR larval tissue (3–7 larvae per biological replicate, n = 8) using the GenElute Universal Total RNA Purification Kit (Sigma-Aldrich, St. Louis, MO, USA). A NanoDrop spectrophotometer (ND-1000, Thermo Fisher Scientific, Waltham, MA, USA) was used to estimate RNA purity and quantity. DNase-treated RNA was used as template for reverse transcription and first-strand cDNA synthesis with PrimeScript Reverse Transcriptase (Takara Bio Inc, Kusatsu, Japan). DNase treatment was carried out using the gDNA Eraser (Perfect Real Time) following manufacturer’s instructions (Takara Bio Inc). For gene expression analysis, 2 μl of undiluted cDNA (i.e., the equivalent of 100 ng total RNA) served as template in a 20 μl qRT-PCR using the TB Green Premix Ex Taq II (Tli RNaseH Plus) kit (Takara Bio Inc) and the Roche LightCycler 96 system (Roche, Basel, Switzerland), according to manufacturer’s instructions. Transcript abundances of the following WCR genes were analysed: DvvGr1, DvvGr2, and DvvGr3 (Rodrigues et al., 2016). Actin was used as reference gene to normalize expression data across samples. Relative gene expression levels were calculated by the 2-ΔΔCt method (Livak and Schmittgen, 2001). The following primers were used: DvvGr1-F CGTTAATTTAGCTGCTGTGG, DvvGr1-R GTTTTCTGTTGCTAGAGTTGC, DvvGr2-F GAACTAAGCGAGCTCCTCCA, DvvGr2-R CAGAAGCACCATGCAATACG, DvvGr3-F GCAACGCTTTCAGCTTTACC, DvvGr3-R GTGCATCGTCATTCATCCAG, DvvActin-F TCCAGGCTGTACTCTCCTTG, and DvvActin-R CAAGTCCAAACGAAGGATTG.

CO2 measurements

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CO2 was quantified by an infrared CO2 gas analyser or by gas chromatography coupled to a flame ionization detector (GC-FID). In the first case, air samples were collected by a micropump (Intelligent Subsampler TR-SS3, Sable Systems International, Las Vegas, NV, USA) connected to an airstream selector (RM8 Intelligent Multiplexer, V5, Sable Systems International, Las Vegas, NV, USA) controlled by a computer via a Universal Interface (UI-2) and the Expedata software version 1.2.6 (Sable Systems International, Las Vegas, NV, USA). The sampled air passed through an infrared CO2 gas analyser (LI 7000, Li-Cor Inc, Lincoln, NE, USA) (Frei et al., 2017). In the second case, air samples were collected by using a syringe equipped with a Luer connector, a stopcock valve, and a needle. Also, 3 ml of air samples were immediately injected and CO2 was analysed by a GC-FID (Shimadzu GC-8) equipped with a methanizer (VWR, Radnor, PA, USA) and a Poropack N column. Nitrogen was used as carrier gas (400 kPa). After injection, the column temperature was maintained at 100°C for 1.3 min, and then increased to 130°C at a rate of 30°C/min and maintained at this temperature for 4 min. The FID temperature was set at 250°C.

Root volatile measurements

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To measure root volatiles, three 4-day-old maize seedling were transplanted into moist white sand (Migros, Switzerland) in spherical glass pots (7 cm diameter, Verre and Quartz Technique SA, Neuchâtel, Switzerland). To boost volatile release, the roots were damaged mechanically before transplantation by briefly twisting them. The pots were wrapped in aluminium foil. Clean humidified air was pushed through the pots at a rate of 1 l·min−1 and pulled through Porapak filters (25 mg of Porapak adsorbent, 80–100 mesh; Alltech Assoc., Deerfield, IL, USA) at a rate of 0.6 L·min−1. Root volatiles were collected over 6 hr. After this period, the filters were eluted with 150 μl of dichloromethane, and N-octane and nonyl-acetate (Sigma, Buchs, Switzerland) were further added as internal standards (200 ng in 10 μl dichloromethane). The root volatiles were analysed by gas chromatography coupled to mass spectrometry (Agilent 7820A GC coupled to an Agilent 5977E MS, Agilent Technologies, Santa Clara, CA, USA). The aliquot was injected in the injector port (230°C) and pulsed in a spitless mode onto an apolar column (HP-5MS 5% Phenyl Methyl Silox, 30 m × 250 μm internal diameter × 0.25 μm film thickness, J&W Scientific, Agilent Technologies SA, Basel, Switzerland). Helium at a constant flow of 1 ml·min−1 (constant pressure 8.2317 psi) was used as carrier gas. After injection, the column temperature was maintained at 40°C for 3.5 min, and then increased to 100°C at a rate of 8°C/min and subsequently at 5°C/min to 230°C, followed by a post run of 3 min at 250°C. Volatile identification was obtained by comparing mass spectra with those of the NIST17 Mass Spectra Library, and relative quantities for the major compounds were calculated based on the peak areas of the internal standards.

Belowground olfactometer experiments with DvvGr1-, DvvGr2-, and DvvGr3-silenced WCR larvae

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To determine whether silencing putative CO2 receptor genes impairs the ability of WCR larvae to behaviourally respond to CO2, we silenced DvvGr1, DvvGr2, and DvvGr3 as described above and evaluated larvae responses to CO2 in dual-choice experiments using belowground olfactometers. Larvae that were fed bacteria that express dsRNA that targets GFP were used as controls (herein referred to as wild type larvae; WT). The belowground olfactometers consist of two L-shaped glass pots (5 cm diameter, 11 cm deep) connected to a detachable central glass tube (24–29 mm diameter, 8 cm in length) by detachable Teflon connectors (Verre and Quartz Technique SA, Neuchâtel, Switzerland) (Figure 2B). The Teflon connectors contained wire mesh screens (2300 mesh, Small Parts Inc, Miami Lakes, FL, USA) to restrain the larvae from moving into the plants. The central glass tubes remained empty to only allow volatile compounds to diffuse through the central glass tubes. The central glass tubes have an access port in the middle to allow the release of insects (Figure 2B). Insects can freely move inside the central glass tube (8 cm in length) and reach the metal wire screens. For further technical specifications regarding the belowground olfactometers, refer to Rasmann et al., 2005 and Robert et al., 2012a. To increase CO2 levels in one side of the olfactometers, we used carbonated water as a CO2 source (Bernklau and Bjostad, 1998a; Huang et al., 2017; Jewett and Bjostad, 1996). For this, a plastic cup containing 50 ml of carbonated water (Valais, Aproz Sources Minérales, Aproz, Switzerland) was placed in one L-shaped glass pot and a plastic cup containing 50 ml of distilled water was placed in the opposite pot. L-shaped glass pots did not contain any substrate to allow CO2 to freely diffuse into the central glass tubes (Figure 2B). Ten minutes after placing the cups into the L-shaped glass pots, L-shaped glass pots were connected to the central glass tubes and six larvae were released in the middle of the olfactometer (red arrow, Figure 2B). Larval positions were recorded 1 hr after their release. Insect preference for a given treatment was considered when the larvae were found at a distance of 1 cm or less from the odour source; this is 1 cm apart from the wire mesh. Seven olfactometers per larval type and experiment were assessed. Olfactometers were covered with aluminium foil to reduce light disturbance to the larvae. Aluminium foil was removed shortly before evaluating larval positions. The experiment was repeated twice. CO2 levels on each arm of the olfactometer were measured by GC-FID as described above. Air samples to determine CO2 concentrations were collected by using a syringe equipped with a Luer connector, stopcock valve, and needle. Prior to sampling, we first connected the Teflon connectors to the L-shaped glass pots and closeed them with parafilm. Then, we placed a plastic cup containing either 50 ml of carbonated water or 50 ml of distilled water. Ten minutes after, we pierced the parafilm with the needle and collected 3 ml of air samples using the syringe and immediately injected the samples to the GC-FID for CO2 measurements.

Insect responses to methyl anthranilate

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To determine whether silencing the DvvGr2 carbon dioxide receptor affects larval responses to a plant volatile other than CO2, we evaluated larval responses to methyl anthranilate. For this, we evaluated insect preferences for seedling roots or for seedling roots placed next to a filter paper disc treated with methyl anthranilate following a similar experimental procedure as described by Bernklau et al., 2019. To this end, either five 2nd–3rd instar WT WCR larvae or five 2nd–3rd instar DvvGr2-silenced WCR larvae were released in the middle of a moist sand-filled Petri plate (9 cm diameter, Greiner Bio-One GmbH, Frickenhausen, DE) where they encountered two 3-day-old maize seedling roots in one side or two 3-day-old maize seedlings roots and a filter paper disc (0.5 cm diameter, Whatman no. 1, GE Healthcare Life Sciences, UK) treated with 10 µl of methyl anthranilate solution (10 mg/ml of water) in the opposite side. Methyl anthranilate was purchased from Sigma (CAS: 134-20-3; Sigma Aldrich Chemie, Switzerland). Sand layers were 3–4 mm high and allowed the larvae to move freely in and on the substrate. Ten Petri plates per larval type with five larvae each were evaluated (n = 10). Petri plates were covered with black plastic sheets to avoid light disturbance to the insects. Larval positions were recorded 1 hr after releasing the larvae. Insect preference for a given treatment was considered when the larvae were found on the roots or in contact with the filter paper discs.

Insect responses to Fe(III)(DIMBOA)3

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To determine whether silencing the DvvGr2 carbon dioxide receptor affects larval responses to plant metabolites other than CO2, we evaluated larval responses to Fe(III)(DIMBOA)3. For this, we evaluated insect preferences for filter paper discs impregnated with Fe(III)(DIMBOA)3 or for filter paper discs treated with water following the procedure described by Hu et al., 2018 with minor modifications. To this end, we released either six 2nd–3rd instar WT WCR larvae or six 2nd–3rd instar DvvGr2-silenced WCR larvae in the middle of a moist sand-filled Petri plate (6 cm diameter, Greiner Bio-One GmbH, Frickenhausen, DE) where they encountered a filter paper disc (0.5 cm diameter, Whatman no. 1, GE Healthcare Life Sciences, UK) treated with 10 μl of Fe(III)(DIMBOA)3 (1 µg/ml of water) or, on the opposite side, a filter paper disc treated with water only. Twenty Petri plates with six larvae each were evaluated (n = 20). Fe(III)(DIMBOA)3 was prepared fresh by mixing FeCl3 and DIMBOA at a 1:2 ratio as described by Hu et al., 2018. Petri plates were covered with black plastic sheets to avoid light disturbance to the insects. Larval preferences were recorded 1 hr after releasing the larvae. Insect preference for a given treatment was considered when the larvae were found in contact with the filter paper discs.

Insect responses to soluble sugars

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To determine whether silencing the DvvGr2 carbon dioxide receptor affects larval responses to plant metabolites other than CO2, we evaluated larval responses to soluble sugars. For this, we evaluated insect preferences for a mixture of glucose, fructose, and sucrose following the procedure described by Bernklau et al., 2018 with minor modifications. Briefly, we released either six 2nd–3 instar WT WCR larvae or six 2nd–3rd instar DvvGr2-silenced WCR larvae in the middle of a moist sand-filled Petri plate (6 cm diameter, Greiner Bio-One GmbH, Frickenhausen, DE) where they encountered a filter paper disc (0.5 cm diameter, Whatman no. 1, GE Healthcare Life Sciences, UK) treated with 10 μl of a mixture of glucose, fructose, and sucrose (30 mg/ml of each sugar), or, on the opposite side, a filter paper treated with water only. Twenty Petri plates with six larvae each were assayed (n = 20). Petri plates were covered with black plastic sheets to avoid light disturbance to the insects. Larval preferences were recorded 3 hr after release. Insect preference for a given treatment was considered when the larvae were found in contact with the filter paper discs.

Dose-dependent insect responses to CO2

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To determine whether silencing the DvvGr2 carbon dioxide receptor affects larval responses to CO2 and to determine the range of behaviourally active CO2 concentrations, we evaluated larval responses to different concentrations of CO2 in dual-choice experiments using belowground olfactometers. CO2 levels were increased in one side of the olfactometer by delivering CO2-enriched synthetic air (1% CO2, Carbagas, Switzerland). For this, the L-shaped glass pots were closed on top using parafilm during CO2 delivery. A manometer connected to the synthetic air bottle allowed to fine-tune CO2 delivery rates and concentrations. CO2 levels were measured using a gas analyser (Li7000, Li-Cor Inc, Lincoln, NE, USA) as described above. CO2 levels were increased at different levels from 22 to 1832 ppm above ambient CO2 levels. Once the desired CO2 concentrations were reached, CO2 delivery was terminated, and the olfactometers were assembled by connecting two L-shaped glass pots to a central glass tube as described above. Immediately after this, either six 2nd–3rd instar WT WCR larvae or six 2nd–3rd instar DvvGr2-silenced WCR larvae were released in the middle of the central glass tubes. Larval positions were evaluated within 10 min of release. Experiments were conducted in a dark room to reduce light disturbance to the larvae. Red-light headlamps were used by the experimenters during the experiment. Insect preference for a given treatment was considered when the larvae were found at a distance of 1 cm or less from the odour source; this is 1 cm apart from the wire mesh. Three olfactometers per larval type and six larvae per olfactometer were assayed (n = 3).

Insect motility and speed experiments

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To determine whether silencing the DvvGr2 carbon dioxide receptor affects larval motility and speed, larval behaviour and the trajectories followed by individual larvae in open Petri plates that contained either maize root pieces or that were outfitted with a CO2 point releaser in the middle were evaluated. In the first experiment, two root pieces (3–4 cm long) of 4-day-old maize seedlings were placed at the rim of a Petri plate lined with moist filter paper. Then, on the opposite rim (i.e., 9 cm apart), either one 2nd–3rd instar WT WCR larvae or one 2nd–3rd instar DvvGr2-silenced WCR larvae was released. The trajectories followed by the insects and the time required to reach the roots were evaluated. The trajectories followed by the insects were drawn on circular pieces of papers of 9 cm diameter. Six Petri plates with one larva each were assayed (n = 6). In the second experiment, CO2 point releasers were installed in the centre of Petri plates (9 cm diameter, Greiner Bio-One, Austria). For this, Petri plates were pierced with a hot metal needle. Then, another needle that released CO2 at 581 ppm, resulting in CO2 concentrations 60 ppm above ambient CO2 levels, was inserted in the resulting whole. CO2 levels were adjusted using a manometer connected to the synthetic air bottle. CO2 levels were measured using a gas analyser (Li7000, Li-Cor Inc, Lincoln, NE, USA) as described above. Once the desired CO2 concentration was reached, either one 2nd–3rd instar WT WCR larva or one 2nd–3rd instar DvvGr2-silenced WCR larva was released at the rim of the Petri plates (i.e., 4.5 cm apart from the CO2 point releaser). Petri plates were lined with moist filter paper (9 cm diameter, GE Healthcare, UK). Insect behaviour was observed for 3 min, the trajectories followed by the insects during this time were drawn on circular pieces of papers of 9 cm diameter, and the time spent in close contact with the CO2 point releaser was quantified. Six Petri plates with one larva each were assayed (n = 6). Both experiments were conducted in a dark room to reduce light disturbance to the larvae. Red-light headlamps were used by the experimenters during the experiment. The pieces of paper with the drawings of the insect trajectories were scanned. The resulting images were analysed in ImageJ 1.53a to determine the distances crawled by the insects.

Host location experiments using belowground olfactometers

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To determine the importance of plant-associated CO2 for host location by WCR larvae and to test for distance-specific effects, we evaluated host location ability of WCR larvae in dual-choice experiments using belowground olfactometers (Figure 5). To specifically investigate the importance of plant-associated CO2 for host location, preferences of CO2-sensitive and CO2-insensitive insects for intact plant odours and for plant odours without CO2 were evaluated. CO2 was experimentally removed using soda lime (Carl Roth, Karlsruhe, Germany). For this, layers of 5 g of soda lime granules (2–4 mm) were placed between the metal wire screens of the Teflon connectors and the sand contained in the L-shaped glass pots. To test for distance-specific effects, we used two olfactometer types that were otherwise the same but differed in the length of their arms (Figure 5). General specifications of the olfactometers are described above. One set of olfactometers has short arms that allowed for the release of larvae at 9 cm (Figure 5A) from plant volatile sources, and the other one has long arms that allow to release the larvae at 18 cm (Figure 5B) from plant volatiles sources. Insect larvae can move freely into the central glass tube and reach the metal wire screens located at both ends of the central glass tube. L-shaped glass pots were covered with aluminium foil, filled with sand, and one 3-week-old maize plant was transplanted 48 hr before the experiments. L-shaped glass pots without plants were treated similarly. Olfactometers remained detached until shortly before the experiments. Thirty minutes before the experiments, soda lime layers were applied and one L-shaped glass pot with a plant and one L-shaped glass pot without a plant were connected to the central glass tubes. Soda lime layers were used in both sides of the olfactometers. Olfactometers without soda lime served as controls. Then, either six 2nd–3rd instar WT WCR larvae or six 2nd–3rd instar DvvGr2-silenced WCR larvae were released. Olfactometers were covered with aluminium foil to reduce light disturbance to the larvae. Aluminium foil was removed shortly before evaluating larval positions. Larval positions were recorded 1 hr after their release. Insect preference for a given treatment was considered when the larvae were found at least 1 cm from the odour source; this is 1 cm apart from the wire mesh. Four olfactometers with six larvae each were assayed (n = 4). CO2 levels were measured using a gas analyser (Li7000, Li-Cor Inc, Lincoln, NE, USA) as described above.

Host location experiments using soil-filled trays

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To determine the importance of plant-associated CO2 for host location by WCR larvae and to test for distance-specific effects, host location by CO2-sensitive and CO2-insensitive insects was evaluated in soil-filled trays (Figure 7). For this, four or five 2-to 3-week-old maize plants were transplanted into custom-made fabric pockets (12 × 3 × 5 cm) made out of volatile-permeable fabrics (Trenn-Vlies, GeoTex Windhager, Switzerland) filled with soil (Selmaterra, Bigler Samen AG, Thun, Switzerland). The plants were transplanted into the fabric pockets, and the fabric pockets were placed in a corner of plastic trays (80 cm × 15 cm × 4.5 cm) (Migros Do it + Garden, Switzerland) containing soil 24 hr before the experiments. Then, 20 second instar WT WCR larvae or 20 second instar DvvGr2-silenced WCR larvae were released at 16, 32, 48, or 64 cm from the plants. Larval release points are indicated by arrows (Figure 7B). Eight hours after releasing the larvae, their positions were recorded by carefully removing the soil at each tray zone and inspecting it in search for the insects. Six trays per larval type and distance with 20 larvae each were assayed (n = 6). CO2 levels in the soil gas phase of each tray zone were measured by GC-FID as described above.

Host location experiments with differentially fertilized plants

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Optimally fertilized plants emit higher levels of respiratory CO2 than suboptimally fertilized plants (Zhu and Lynch, 2004). To test whether WCR larvae orient towards and prefer optimally fertilized maize plants and to evaluate the importance of CO2 in this context, host location by CO2-sensitive and CO2-insensitive insects and preference for plants that were differentially fertilized was evaluated. To this end, maize plants were fertilized with three doses of fertilizer: 0.1% (optimally fertilized), 0.05% (medium fertilized), or 0.01% (low fertilized). For this, Plantaaktiv 16+6+26 Typ K fertilizer (Hauert HBG Dünger AG, Grossaffoltern, Switzerland) was dissolved to the abovementioned concentrations and applied following manufacturer’s indications. Fertilizer macro- and micronutrient composition are described above (see ‘Plants and planting conditions’). For the choice experiments, plants were grown under the different fertilizer regimes. Twenty-four hours before the choice experiment, five 15-day-old, optimally fertilized plants were re-planted into fabric pockets (described above) and transferred to one corner of an 80 cm long plastic tray (Migros Do it + Garden, Switzerland) filled with soil (Figure 8A, B). At the opposite side, plants grown either under low or medium fertilizer regimes were equally re-planted and transferred. Then, 20 second instar WCR larvae were released in the middle of the tray (zone 3, red arrows). Six independent trays per larval type and fertilizer regime pair were evaluated (n = 6). Eight hours after releasing the larvae, larval positions were recorded.

Effect of plant nutritional status on larval growth

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To test whether larval preference for optimally fertilized plants is reflected in their growth, we measured larval weights of larvae feeding on roots of plants that were grown under the different fertilizer regimes. Fertilizer regimes are described above. For this, seven 1st instar larvae were released into solo cups (30 ml, Frontier Scientific Services, Inc, DE) containing approximately 2 g of organic soil (Selmaterra, Bigler Samen AG, Thun, Switzerland). Fresh roots of 15-day-old plants were provided everyday ad libitum. Roots were washed thoroughly to remove fertilizer traces from the root surface. Twenty solo cups per treatment were included (n = 20). Eight days after the beginning of the experiment, larvae were weighed using a micro balance. Four to seven larvae were recovered per experimental unit at the end of the experiment.

Statistical analyses

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Differences in gene expression levels, larval performance, and carbon dioxide concentrations were analysed by either Student’s t tests or by one-way ANOVA using Sigma Plot 12.0 (SystatSoftware Inc, San Jose, CA, USA). Normality and equality of variance were verified using Shapiro–Wilk, Levene's, and Brown–Forsythe tests. Holm–Sidak post hoc tests were used for multiple comparisons. Data sets from experiments that did not fulfil the assumptions for ANOVA were natural log‐, root square‐, or rank‐transformed before analysis. Carbon dioxide concentrations and differences in larval preference were assessed using GLM under binomial distribution and corrected for overdispersion with quasi-binomial function when necessary followed by analysis of deviance and FDR-corrected post hoc tests. All analyses were followed by residual analysis to verify the suitability of the error distribution and model fitting. All The above analyses were conducted using R 3.2.2 (43) using the packages ‘lme4’, ‘car’, ‘lsmeans’, and ‘RVAideMemoire’ (Bates et al., 2014; Fox and Weisberg, 2011; Herve, 2015; Lenth, 2016; R Development Core Team, 2014).

Data availability

All data that support the conclusions are given in form of figures/tables within the manuscript. Raw data sets are provided as source data files.

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    Los Angeles, USA: Sage Publications.
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Article and author information

Author details

  1. Carla CM Arce

    Institute of Biology, University of Neuchâtel, Neuchâtel, Switzerland
    Contribution
    Resources, Formal analysis, Investigation, Methodology, Writing - original draft, Writing - review and editing
    Contributed equally with
    Vanitha Theepan
    Competing interests
    No competing interests declared
    ORCID icon "This ORCID iD identifies the author of this article:" 0000-0002-1713-6970

  2. Vanitha Theepan

    Institute of Plant Sciences, University of Bern, Bern, Switzerland
    Contribution
    Investigation
    Contributed equally with
    Carla CM Arce
    Competing interests
    No competing interests declared

  3. Bernardus CJ Schimmel

    Institute of Plant Sciences, University of Bern, Bern, Switzerland
    Contribution
    Investigation, Writing - review and editing
    Competing interests
    No competing interests declared

  4. Geoffrey Jaffuel

    Institute of Biology, University of Neuchâtel, Neuchâtel, Switzerland
    Contribution
    Investigation
    Competing interests
    No competing interests declared

  5. Matthias Erb

    Institute of Plant Sciences, University of Bern, Bern, Switzerland
    Contribution
    Conceptualization, Formal analysis, Supervision, Funding acquisition, Methodology, Writing - original draft, Writing - review and editing
    For correspondence
    matthias.erb@ips.unibe.ch
    Competing interests
    No competing interests declared
    ORCID icon "This ORCID iD identifies the author of this article:" 0000-0002-4446-9834

  6. Ricardo AR Machado

    1. Institute of Biology, University of Neuchâtel, Neuchâtel, Switzerland
    2. Institute of Plant Sciences, University of Bern, Bern, Switzerland
    Contribution
    Conceptualization, Resources, Data curation, Formal analysis, Supervision, Funding acquisition, Validation, Investigation, Visualization, Methodology, Writing - original draft, Writing - review and editing
    For correspondence
    ricardo.machado@unine.ch
    Competing interests
    No competing interests declared
    ORCID icon "This ORCID iD identifies the author of this article:" 0000-0002-7624-1105

Funding

H2020 Marie Skłodowska-Curie Actions (794947)

  • Bernardus CJ Schimmel

Schweizerischer Nationalfonds zur Förderung der Wissenschaftlichen Forschung (155781)

  • Matthias Erb

Schweizerischer Nationalfonds zur Förderung der Wissenschaftlichen Forschung (186094)

  • Ricardo AR Machado

The funders had no role in study design, data collection and interpretation, or the decision to submit the work for publication.

Acknowledgements

We thank Evangelia Vogiatzaki and Celine Terrettaz for technical assistance, and the members of the Research Section Biotic Interactions of the Institute of Plant Sciences of the University of Bern, Switzerland, for their support and helpful discussions. This project was supported by the University of Bern, a European Union Horizon 2020 Marie Sklodowska-Curie Action (MSCA) Individual Fellowship (grant no. 794947 to BCJS), and the Swiss National Science Foundation (grant no. 155781 to ME, grant no. 186094 to RARM).

Version history

  1. Received: December 8, 2020
  2. Accepted: March 8, 2021
  3. Version of Record published: April 20, 2021 (version 1)

Copyright

© 2021, Arce et al.

This article is distributed under the terms of the Creative Commons Attribution License, which permits unrestricted use and redistribution provided that the original author and source are credited.

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  1. Carla CM Arce
  2. Vanitha Theepan
  3. Bernardus CJ Schimmel
  4. Geoffrey Jaffuel
  5. Matthias Erb
  6. Ricardo AR Machado
(2021)
Plant-associated CO2 mediates long-distance host location and foraging behaviour of a root herbivore
eLife 10:e65575.
https://doi.org/10.7554/eLife.65575

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