From an herbivore's first bite, plants release herbivory-induced plant volatiles (HIPVs) which can attract enemies of herbivores. However, other animals and competing plants can intercept HIPVs for their own use, and it remains unclear whether HIPVs serve as an indirect defense by increasing fitness for the emitting plant. In a 2-year field study, HIPV-emitting N. attenuata plants produced twice as many buds and flowers as HIPV-silenced plants, but only when native Geocoris spp. predators reduced herbivore loads (by 50%) on HIPV-emitters. In concert with HIPVs, plants also employ antidigestive trypsin protease inhibitors (TPIs), but TPI-producing plants were not fitter than TPI-silenced plants. TPIs weakened a specialist herbivore's behavioral evasive responses to simulated Geocoris spp. attack, indicating that TPIs function against specialists by enhancing indirect defense.https://doi.org/10.7554/eLife.00007.001
As the population of the world continues to increase beyond 7 billion, and agricultural pests continue to rapidly evolve resistance to pesticides, it is becoming ever more important to cultivate arable land in a way that is sustainable for both humans and the environment. A better understanding of the different mechanisms used by wild plants to deter herbivores will help to increase crop production without harming the environment.
Plants use both direct and indirect methods to fend off herbivores. Direct defense methods include the production of chemicals that are toxic to herbivores or give them indigestion, and the growth of sticky prickles and spines that can injure or kill the herbivore. Indirect defense methods, on the other hand, generally rely on the plant attracting organisms that are either predators or parasites of the herbivore.
Plants produce odors known as herbivory-induced plant volatiles (HIPVs) that are thought to offer indirect defense against herbivores by betraying their location to predators and parasites. However, HIPVs also influence other members of the ecological community, sometimes in ways that are detrimental to plants. Moreover, despite 30 years of research, no study has demonstrated that HIPVs increase the fitness of a plant, so it is unclear what they have evolved to do.
Now, a 2-year field study by Schuman et al. has shown plants that emit green leaf volatiles (which are a type of HIPV) produce twice as many buds and flowers—a measure of fitness—as plants that have been genetically engineered not to emit green leaf volatiles. This study was conducted with Nicotiana attenuata, which is a wild tobacco plant that is often targeted by Manduca sexta, a type of moth that is also known as the tobacco hornworm. Green leaf volatiles only increased plants' fitness when various species of Geocoris—a bug that preys on Manduca sexta—reduced the number of herbivores by a factor of two. This is the first evidence that HIPVs offer indirect defense against herbivores.
Schuman et al. also studied the effects of molecules called protease inhibitors that are thought to function as direct defenses by making it difficult for herbivores to digest plants. They found that the ability to produce protease inhibitors did not increase the fitness of plants under herbivore attack; however, tobacco hornworms that had been fed plants containing protease inhibitors were found to be more sluggish in response to attack, which suggests that protease inhibitors can enhance the indirect defenses of plants. The results suggest that employing both direct and indirect defenses—such as a combination of biological pesticides and genetic engineering to produce both HIPVs and protease inhibitors—is the best approach for defending agricultural plants against pests.https://doi.org/10.7554/eLife.00007.002
Plant indirect defenses are traits that disable or remove herbivores by manipulating tri-trophic interactions to the advantage of the plant (Price et al., 1980). They attract and inform the third trophic level, predators or parasitoids, resulting in increased attacks on herbivores (Turlings and Wäckers, 2004). Indirect defenses are widespread and include domatia, extrafloral nectar, and food bodies which provide shelter and nutrition for predators and parasitoids, as well as herbivory-induced plant volatiles (HIPVs) which convey information about feeding herbivores (Heil, 2008). Field studies with the native tobacco Nicotiana attenuata, a desert annual, and with maize have shown that HIPVs can reduce herbivore loads by 24% to more than 90%, by increasing both predation and parasitization of herbivores (Kessler and Baldwin, 2001; Rasmann et al., 2005; Halitschke et al., 2008; Degenhardt et al., 2009; Allmann and Baldwin, 2010) and deterring herbivore oviposition (Kessler and Baldwin, 2001).
If HIPVs really function as defenses, they should increase Darwinian fitness, defined as successful reproduction, for plants under herbivore attack (Karban and Baldwin, 1997). But because HIPVs can be perceived by many other members of the ecological community—from herbivores, pollinators, predators and parasitoids to competing or parasitic plants—it is not clear whether HIPVs increase plant fitness in nature (Dicke and Baldwin, 2010; Kessler and Heil, 2011). The field studies described above have either spanned too short a time to reveal Darwinian fitness benefits, or have not reported fitness data at all (Kessler and Baldwin, 2001; Rasmann et al., 2005; Halitschke et al., 2008; Degenhardt et al., 2009; Allmann and Baldwin, 2010). Two laboratory studies showed that parasitization of herbivores can increase plant reproduction (van Loon et al., 2000; Hoballah and Turlings, 2001), but the parasitization in these studies was not mediated by HIPVs. Hence three decades after their description, it remains unclear whether HIPVs are really indirect defenses.
Long-term field studies comparing HIPV-emitting vs -deficient plants are required in order to demonstrate a defensive function for HIPVs. Experimental additions of pure volatiles or mixes to plants growing in nature has worked well to test short-term effects of specific compounds (Kessler and Baldwin, 2001; Allmann and Baldwin, 2010), but only endogenously produced HIPV emissions can ensure specific, lasting and consistent differences under field conditions. Most evidence for the utility of HIPVs comes from studies in which predators and parasitoids learn to associate HIPVs with prey; naïve predators and parasitoids are just as likely to respond to HIPVs as not to respond (Allison and Hare, 2009). Thus the inducibility of HIPV emission, which ensures association with herbivore feeding, is likely essential for HIPV function, but it is difficult to engineer (Kos et al., 2009). Engineered constitutive HIPV emissions have been used, either on predators and parasitoids trained to associate target volatiles with prey in short-term laboratory experiments (Kappers et al., 2005; Schnee et al., 2006), or in set-ups in which target volatiles are always associated with prey (Rasmann et al., 2005; Degenhardt et al., 2009). When plants are engineered constitutively to emit HIPVs, they no longer provide accurate information about the location of feeding herbivores, and predators will not associate these signals with prey in nature. Genetically silencing the biosynthesis of HIPVs, however, permits naturally inducible wild-type (WT) plants to serve as HIPV emitters, for comparison with transformed lines lacking specific volatile components (Halitschke et al., 2008; Skibbe et al., 2008). Furthermore, field experiments that manipulate the production of HIPVs which not only attract the third trophic level, but also influence the second trophic level (e.g., as feeding stimulants and host location cues), require additional experimental manipulations to preserve the plant-herbivore part of the tritrophic interaction.
When HIPVs do attract the third trophic level, how can herbivores adapt? Many herbivores can outgrow their vulnerability to predators and parasitoids, but plant direct defenses can slow herbivore growth and prolong vulnerability as postulated by the slow growth-high mortality hypothesis (Benrey and Denno, 1997; Williams, 1999; Kessler and Baldwin, 2001, 2004; Kaplan and Thaler, 2011). The solanaceous specialists Manduca sexta and M. quinquemaculata (Lepidoptera, Sphingidae) are resistant to the potent alkaloid toxin nicotine (Wink and Theile, 2002), but sensitive to the nutritional value of plant tissue (Zavala and Baldwin, 2004). Non-toxic protease inhibitor (PI) proteins, which inhibit protein digestion and thus decrease the availability of organic nitrogen in the form of amino acids (Zavala et al., 2008), are widespread in flowering plants (Hartl et al., 2011), and trypsin protease inhibitors (TPIs) slow the growth of M. sexta on N. attenuata (Zavala et al., 2008). However, herbivores can overcome PIs by producing insensitive or desensitized proteases, inactivating or degrading PIs, eating more plant tissue, and eating more nutritious young tissue (Winterer and Bergelson, 2001; Steppuhn and Baldwin, 2007; Zavala et al., 2008). In the latter two cases, PIs could reduce plant fitness. Although TPI-producing N. attenuata plants produce more seeds than TPI-deficient plants when attacked by M. sexta under controlled glasshouse conditions (Zavala and Baldwin, 2004), whether TPIs function as a direct defense in nature is unknown.
We tested the hypotheses that HIPVs and TPIs defend plants in nature by increasing herbivore predation and thereby plant Darwinian fitness. To do so, we monitored the performance, predation and mortality of Manduca spp. (M. sexta and M. quinquemaculata) on wild-type N. attenuata plants and RNAi transformed lines silenced for the production either of a specific group of HIPVs, or of TPIs, and compared the resulting plant reproductive output in terms of bud and flower production (we are not permitted to allow transgenic plants to disperse ripe seed). Because N. attenuata is an annual, opportunistic out-crosser, seeds are produced within one growing season, mostly from fertilization via self-pollen (Sime and Baldwin, 2003), and we can relate bud and flower production to lifetime seed production, which is commonly accepted as a measure of Darwinian fitness (Baldwin, 1998; van Loon et al., 2000; Hoballah and Turlings, 2001).We hypothesized that HIPVs would increase plant reproduction by increasing predation of herbivores, and that TPIs alone would not increase reproduction under herbivore attack, but would either increase predation or increase herbivores' susceptibility to predators. We then assembled a toolbox of wild-type and transgenic lines chosen to test these hypotheses.
We chose a genotype of N. attenuata native to the Great Basin Desert of southwestern Utah. In many years, Manduca spp. larvae cause the most defoliation of N. attenuata plants in this area (Kessler and Baldwin, 2001) and thus the N. attenuata 'UT' genotype is likely adapted to defend against Manduca spp. Eggs and young larvae of Manduca spp. are predated by Geocoris spp. (big-eyed bugs) which occur naturally in the Utah habitat and are attracted to components of N. attenuata's HIPV bouquet (Kessler and Baldwin, 2001; Halitschke et al., 2008; Skibbe et al., 2008). Specifically, Utah Geocoris spp. predators are attracted to the sesquiterpene (E)-α-bergamotene as well as green leaf volatiles (fatty acid-derived C6 aldehydes, alcohols and esters) (Kessler and Baldwin, 2001; Halitschke et al., 2008; Schuman et al., 2009). Green leaf volatiles, or GLVs, can be silenced via a single upstream 13-lipoxygenase, NaLOX2, which specifically supplies lipid hydroperoxides for their production (Allmann et al., 2010). Although GLVs are released upon mechanical damage, the oral secretions (OS) of M. sexta convert 3-(Z)-GLVs to the 2-(E)-structures, resulting in greater Geocoris spp. predation than the damage-induced (Z):(E) ratio (Allmann and Baldwin, 2010). GLVs are released immediately upon damage (Allmann and Baldwin, 2010) and may therefore be a 'first line of defense'.
Like GLVs, many other HIPVs are also released after mechanical damage, but change in amount or ratio upon herbivory, and thus GLVs mirror the functional complexity of the total HIPV blend. Furthermore, GLVs prime or directly regulate responses in neighboring plants (Kessler et al., 2006; Paschold et al., 2006), attract herbivores as well as predators (Halitschke et al., 2008), and are important cues for pollinating and ovipositing moths (Kessler and Baldwin, 2001, 2006; De Moraes et al., 2001; Fraser et al., 2003), thus performing several roles which may harm or benefit plant fitness in addition to their role in attracting predators. Perhaps most significantly, GLVs also stimulate Manduca spp. feeding, and silencing plant GLV production results in reduced herbivore damage (Halitschke et al., 2004; Meldau et al., 2009). All these qualities made the manipulation of GLV emissions an ideal means to test rigorously the fitness consequences of HIPV emissions and to evaluate whether these emissions can truly be considered defensive.
We chose a line of irPI plants with no detectable TPI activity (Steppuhn and Baldwin, 2007), and a line of irLOX2 plants with GLV emissions <20% of WT (Allmann et al., 2010); non-target defense metabolites are not affected in either line (Steppuhn and Baldwin, 2007; Allmann and Baldwin, 2010), including emission of (E)-α-bergamotene measured in a glasshouse characterization of all lines prior to field release (see 'Non-target metabolites are not affected in irLOX2, hemi-irLOX2 or irPI plants'). Because of the importance of GLVs for the plant-herbivore interaction, we used both homozygous (Allmann et al., 2010) and hemizygous irLOX2 plants to provide different levels of GLV silencing. Hemizygous (hemi-) irLOX2 plants were created by crossing homozygous irLOX2 and irPI plants, but the irPI construct was not active in this cross (Figure 1 see 'Discussion').
The irPI plants (Steppuhn and Baldwin, 2007) had no detectable TPI activity in the glasshouse or throughout the field experiment in 2011, and PI transcripts accumulated to only 0.3% of WT levels in irPI (transcripts, N=5, p<0.001 in Scheffe post hoc tests following two-way ANOVAs on log2-transformed data with factors W+OS treatment and genotype: treatment F1,29=75.909, p<0.001; genotype F3,29=174.077, p<0.001); in contrast, TPI activity and PI transcripts were similar to WT plants in irLOX2 and hemi-irLOX2 (transcripts, N=5, p>0.2 in Scheffe post hoc tests following two-way ANOVAs on log2-transformed data with factors W+OS treatment and genotype; activity, N=10–17, p>0.05 in one-way ANOVAs with factor genotype) (Figure 1).
We assessed GLV production by hexane extraction of GLVs from frozen leaf tissue, and GLV emission by GC analyses of leaf headspaces. GLVs in hemi-irLOX2 plants were reduced to levels similar to those in irLOX2 plants, but hemi-irLOX2 plants still produced detectable amounts of (Z)-3-hexenol (Figures 2 and 3). The dominant GLV in hexane tissue extracts was (E)-hex-2-enal, and (Z)-hex-3-en-1-ol was additionally quantifiable as a minor component. Only (E)-hex-2-enal was quantifiable in extracts from field-grown plants on May 28, 2011, and was below quantifiable levels in irLOX2 and hemi-irLOX2 plants, but detectable in pooled samples from hemi-irLOX2 (Figures 2 and 3). Extracts from later in the season also contained quantifiable amounts of (Z)-hex-3-en-1-ol and hemi-irLOX2 extracts contained up to 50% as much of this alcohol as WT and irPI extracts (N=10, p<0.05 in Scheffe post hoc tests following one-way ANOVAs with factor genotype: June 14, 2011, F2,26=9.556, p=0.001; June 22, 2011, F2,26=12.196, p<0.001; p>0.6 for irPI vs WT in a t-test for May 28 and in Scheffe post hoc tests for June 14 and 22) (Figure 3). Headspace measurements from field- and glasshouse-grown plants detected a similar 80–100% reduction in GLV emissions from irLOX2 and hemi-irLOX2 plants compared to WT and irPI (field, N=3, p=0.024 for hemi-irLOX2 v irPI, p>0.05 for hemi-irLOX2 vs WT and irLOX2 vs irPI and WT, but p=0.939 for irPI vs WT in Scheffe post hoc tests following one-way ANOVA: F3,8=7.346, p=0.011; glasshouse, N=4: irLOX2 and hemi-irLOX2 below limit of detection, p=0.834 for t-test irPI vs WT) (Figure 3), and transcript accumulation of LOX2 was 2% of WT levels in irLOX2 and hemi-irLOX2 (N=5, p<0.001 in Scheffe post hoc tests following two-way ANOVAs on log2-transformed data with factors W+OS treatment and genotype: treatment F1,32=0.021, p=0.887; genotype F3,32=635.477, p<0.001) but unaffected in irPI (p>0.9 in Scheffe post hoc test vs WT) (Figure 3).
For the ‘UT’ genotype of N. attenuata used in our experiments, the induction of all HIPVs except GLVs is mediated by jasmonate signaling (Halitschke and Baldwin, 2003; Kessler et al., 2004). The irPI line A-04-186-1 (Steppuhn and Baldwin, 2007) and irLOX2 line A-04-52-2 (Allmann et al., 2010) have been characterized previously, and neither is affected in jasmonate signaling. Particularly, the emission of (E)-α-bergamotene, the best-characterized HIPV in N. attenuata apart from GLVs (Halitschke et al., 2000; Kessler et al., 2004; Halitschke et al., 2008; Skibbe et al., 2008), does not differ significantly among the lines used (N=4 measured 24–32 hr after W+OS treatment as according to Halitschke et al. (2000) and normalized as a percentage of the internal standard peak: WT, 67.9±17.1%; irPI, 30.2±13.2%; irLOX2, 26.6±5.8%; hemi-irLOX2, 42.7±23.3%; ANOVA: F3,12=1.338, p=0.308). The transformation process itself does not affect plant fitness or competitive ability (Schwachtje et al., 2008), TPI production or volatile emission (Figures 1–3).
We monitored the predation of Manduca spp. larvae and eggs daily, and counted Geocoris spp. individuals around plants every 2–3 days (Geocoris spp. counts, Figure 4). In 2010, we planted into a first-year plot. Although plants were infested with laboratory strain M. sexta larvae (N=51) and baited with M. sexta eggs (N=50) over a 2-week period in 2010 (Figure 4), no Geocoris spp. individuals were observed on this plot through May. There were also no Geocoris spp. observed through May on a nearby, older plot: Geocoris spp. first arrived and began to predate Manduca spp. eggs on the older plot on June 9. In 2011, we planted into the older plot, where we observed Geocoris spp. in May prior to the first infestation (M2, Figure 4).
During infestation M2 (Figure 4), we allowed Geocoris spp. to associate all four plant genotypes with the presence of prey: we infested half of all plants with equal numbers of first-instar M. sexta larvae from the laboratory strain and, because Geocoris spp. predate more from GLV-emitting or-perfumed plants (Kessler and Baldwin, 2001; Halitschke et al., 2008; Allmann and Baldwin, 2010), we supplemented GLV emission from irLOX2 and hemi-irLOX2 plants by placing cotton swabs with lanolin paste containing GLVs representative of the M. sexta-fed N. attenuata headspace (Table 1 Allmann and Baldwin, 2010) adjacent to M. sexta-infested leaves. Swabs containing lanolin with solvent were placed next to irPI and WT as a control. M. sexta larvae were predated at a rate of 12–37% over two 2- to 3-day trials. Geocoris spp. tended to predate more larvae from GLV-supplemented plants (Fisher's exact tests, 35–37% vs 22–27% May 5–6, N=59–60 larvae, p=0.066; 17–21% vs 12% May 13–15, N=92–100 larvae, p=0.069; combined trials, Bonferroni-corrected p=0.0063) (Figure 5).
We removed the cotton swabs and the remaining larvae. We then monitored predation of newly-infested larvae and eggs without GLV supplementation during infestation M3 (Figure 4). We staggered infestation to accommodate differences in plant growth: WT and irPI seedlings were initially larger and therefore were planted into the field on average 3 days earlier than irLOX2 and hemi-irLOX2 plants, so that all plants were planted at a similar size, which is important for even establishment. We therefore re-infested WT and irPI plants earlier after M2, to allow irLOX2 and hemi-irLOX2 plants to catch up in their growth to WT and irPI before re-infestation, so as not to bias further assays. However, we left M. sexta larvae on irLOX2 and hemi-irLOX2 as long as on WT and irPI, and we made several control measurements to ensure that differences in Geocoris spp. predation were not due to our staggering of infestation: we counted Geocoris spp. populations around all genotypes over this period (Table 2) and saw that they were not different (p>0.05 in Fisher's exact tests), indicating that Geocoris spp. continued to explore irLOX2 and hemi-irLOX2 plants but not to predate from them over a week of infestation followed by 5 days of M. sexta egg predation assays (during which M. sexta eggs were simultaneously applied to all genotypes); and we followed predation of M. sexta larvae from all four genotypes in parallel over 1 week, during which irLOX2 and hemi-irLOX2 were infested with more larvae than WT and irPI due to sustained higher predation rates on WT and irPI; but predation remained higher on WT and irPI.
Predation of both larvae and eggs without GLV supplementation was two to four times as great on GLV-emitting WT and irPI plants: 43%/60% (WT/irPI) for larvae and 34%/39% for eggs, vs 17%/33% (irLOX2/hemi-irLOX2) for larvae and 9%/20% for eggs (Fisher's exact tests: N=30 larvae, p=0.047 for irLOX2 vs WT, p=0.069 for hemi-irLOX2 vs irPI; N=88 eggs, p<0.001 for irLOX2 vs WT, p=0.013 for hemi-irLOX2 vs irPI) (Figure 5). Predation was associated with a steady Geocoris spp. population of 16–23 individuals per day within a 5 cm radius around plants (Table 2). However, there was no difference among plant genotypes in the number of Geocoris spp. individuals (p>0.05 in Fisher's exact tests), indicating that Geocoris spp. regularly survey all plants and use GLVs as a short-distance cue to determine which plants harbor prey. Figure 5 shows larval predation rates at the beginning of the assay, when the M. sexta load was comparable across plant genotypes. Over the following week, Geocoris spp. predated a total of 80% of these larvae from WT and irPI vs 47% from irLOX2 (Fisher's exact test, p=0.015 vs WT) and 67% from hemi-irLOX2 (p=0.382 vs irPI).
In summary, Geocoris spp. had the same opportunity to locate M. sexta larvae and eggs on all genotypes, but consistently preferred to predate from GLV-supplemented or -emitting plants.
We took the different number of ‘days in field’ for each plant into account in our comparison of growth and reproduction among genotypes and therefore the staggered planting did not affect this comparison (Figure 6, statistics Table 3). The irLOX2 and hemi-irLOX2 plants suffered, in total, a similar amount of M. sexta damage to WT plants in trials M2 and M3 (Figure 4), and only irPI plants suffered significantly less M. sexta damage (Figure 7).
Reduced predation of M. sexta from irLOX2 and hemi-irLOX2 in trials M2 and M3 in 2011 (Figure 4) correlated with the reduced growth and reproduction of both genotypes, by 30–50% for irLOX2 and 20–30% for hemi-irLOX2 vs WT, although this reduction was also apparent in plants not infested with M. sexta. (Figures 4 and 6, statistics Table 3). In 2010 however, in the absence of predation, there was no difference in stem growth, branching, or bud and flower production among genotypes irrespective of M. sexta infestation (Figure 6, statistics Table 3). Although M. sexta feeding significantly affected growth and reproduction of plants overall, the effect was not significant for irLOX2 or irPI plants in either year (Figure 6, statistics Table 3), possibly due to reduced feeding damage resulting from a lack of TPI-induced compensatory feeding in irPI (Steppuhn and Baldwin, 2007) (Mann-Whitney U-test between irPI and WT on May 28, U=54, p=0.046, Figure 7). Although GLVs are feeding stimulants (Halitschke et al., 2004), we could not measure reduced M. sexta feeding damage in hemi-irLOX2 or irLOX2 (Figure 7). Yet hemi-irLOX2 plants, despite strongly reduced GLVs, still suffered reduced growth and reproduction from Manduca spp. feeding: M. sexta feeding reduced flower production rates by about 50% in WT and by about 30% in hemi-irLOX2 plants in 2010, although the overall reduction was only significant in WT; and reduced bud production significantly for both WT and hemi-irLOX2 by 25–30% in 2011 (Figure 6, statistics Table 3).
We monitored herbivore attack to determine whether GLV-silenced plants suffered different amounts of damage from naturally occurring herbivores, which could also cause differences in their growth and reproduction. All genotypes were attacked by mirid (Tupiocoris notatus) and noctuid herbivores which caused similar amounts of damage across genotypes and years (ca. 15% and 3% of total canopy area, respectively) although irLOX2 plants suffered 60% less mirid and noctuid damage by the end of M3 in 2011 (N=24–28; Bonferroni-corrected Kruskal-Wallis test, noctuids May 5, p=0.027, all pairwise tests Bonferroni-corrected p>0.05; one-way ANOVAs with factor genotype on arcsine-transformed data: mirids May 27, F3,103=5.291, p=0.002, p<0.05 for irLOX2 vs hemi-irLOX2 and irPI in Scheffe post hoc tests, noctuids May 27, F3,103=3.503, p=0.018, all post hoc tests p>0.05; all other comparisons p>0.05; Figures 4 and 7). Reduced herbivore damage on irLOX2 in 2011 could have increased the growth and reproduction of irLOX2 plants relative to WT, but cannot explain why irLOX2 plants instead displayed reduced growth and reproduction. Plants in 2011 were also damaged by flea beetles and grasshoppers (<3% of canopy area, Kruskal-Wallis tests, N=24–28, all comparisons p>0.05, Figure 7).
We cannot exclude the possibility that reduced growth and reproduction of uninfested irLOX2 and hemi-irLOX2 plants in 2011 (Figure 6, statistics Table 3) might have been due to non-herbivory-related factors (e.g., differences in root health corresponding to GLV antimicrobial properties) which did not play a role in 2010. Because of this uncertainty, we conducted assay M4 (Figure 4) in which plants were carefully matched for size and prior reproduction (Figure 8), and this experiment is the more robust basis for our argument that GLV-mediated indirect defense increases plant reproduction.
To ensure that the correlated differences we observed in plant reproduction and M. sexta mortality were due to plant GLV emission and not to different timing and amounts of M. sexta damage, and to avoid the influence of non-herbivory-related factors, we conducted a Manduca spp. predation and plant performance assay during infestations M1 in 2010, and M4 in 2011 (Figure 4) for which all plants used were matched for size, as well as former damage and reproduction as necessary (Figure 8), and infested simultaneously with Manduca spp. neonates. We hypothesized that the 50% lower predation rates of Manduca spp. from GLV-deficient plants (Figure 5), combined with Manduca spp.'s negative effect on growth and reproduction (Figure 6), would result in reduced reproduction for GLV-deficient versus matched GLV-producing plants if Geocoris spp. were present. Homozygous irLOX2 plants were excluded from these 'matched' experiments because they did not suffer reduced growth or reproduction from M. sexta feeding, and because they were too small in comparison to other lines in 2011 (Figure 6).
In both 2010 and 2011, we selected triplets of WT, irPI and hemi-irLOX2 plants similar in size, reproductive output, apparent health, and prior damage; damage from naturally occurring herbivores did not differ among these genotypes (Figure 7). In 2010, matched plants were part of infestation M1 (Figure 4) and thus it was not necessary to control for prior reproduction or M. sexta damage. Plants in 2010 received three lab strain M. sexta larvae per plant to a lower stem leaf. We recorded the mortality of M. sexta larvae and the reproductive output of plants until they began to set unripe seed. No reproductive meristems were removed, but flowers were removed and counted periodically over the first 10 days, as was done during infestation M3 in 2011 (Figures 4 and 6, statistics Table 3), to track plant reproduction while avoiding ripe seed capsules: the distribution of ripe seed is not permitted for genetically modified plants. In the absence of Geocoris spp. in 2010, genotypes did not differ in M. sexta mortality (N=51 larvae)—which in every observed case was due to a failure of the larva to feed—or plant reproduction (N=17 plants) (Figure 9). This, and the fact that flower production did not differ among genotypes in 2011 through infestation M3 despite flower removal (Figure 6), indicates that flower removal itself does not cause a difference among genotypes, and suggests that the other differences among genotypes in growth and reproduction seen in 2011 (Figure 6, statistics Table 3) are real.
In 2011, hemi-irLOX2, irPI and WT plants were matched prior to infestation M4 to exclude differences in growth, reproduction and Manduca spp. damage arising during M. sexta infestations M2 and M3 and from caged Manduca spp. during the egg predation assay (Figures 4, 7, and 8). Instead of regularly removing flowers, we removed all reproductive meristems from matched plants in 2011 by cutting inflorescences at their base. This allowed us to follow a new set of reproductive meristems through to seed set without incurring ripe seed. Because plants were matched prior to the assay, a similar number of reproductive meristems were cut from all plants, and thus all plants were similarly affected by this cutting (Figure 8, see 'Discussion').
Because oviposition by native Manduca spp. moths provided sufficient eggs prior to the beginning of M4 (Figure 4), we decided to conduct this infestation with wild larvae and thereby demonstrate that native larvae, like larvae of the lab strain, are susceptible to GLV-mediated predation. To make M4 a realistic test, we placed one wild Manduca spp. neonate per plant on a lower stem leaf to mimic natural oviposition rates (Kessler and Baldwin, 2001). We again recorded the mortality of Manduca spp. larvae and the new reproductive output of plants until they began to set unripe seed. During the first to third larval instars in which larvae are vulnerable to Geocoris spp. predation (Kessler and Baldwin, 2001), wild Manduca spp. mortality was 38% on hemi-irLOX2 plants vs 62–76% on matched WT and irPI plants; the overall mortality of larvae on all three lines was significantly different (N=21 larvae, Bonferroni-corrected pairwise comparisons by Friedman tests, p<0.01) (Figure 9). Although Manduca spp. mortality on hemi-irLOX2 jumped to 70% in the fourth and semi-final larval instar, this was likely due to predation by whiptail lizards (Cnemidophorus spp.) which were present on the field plot: these lizards predate late-instar Manduca and are attracted to short-chain fatty-acid volatiles produced by the larvae due to ingestion of acyl sugars in plant trichomes (Stork et al., 2011; Weinhold and Baldwin, 2011).
The plants used in M4 had not previously differed in their reproduction except that hemi-irLOX2 plants had produced more flowers than WT, but not irPI plants (Figure 8). By the end of the assay, the hemi-irLOX2 plants had produced 40–50% fewer buds and flowers than matched WT and irPI plants (N=21 plants, p<0.05 in Scheffe post hoc tests for hemi-irLOX2 vs WT and irPI flowers and buds following a repeated-measures MANOVA over all flower and bud counts, Wilks' Lambda for the interaction of line and day: F12,110=2.835, p=0.002) (Figure 9). This reduced bud and flower production was not due to accelerated seed set: unripe seed capsules on hemi-irLOX2 plants were also reduced by 50% (N=21 plants, p=0.021 for hemi-irLOX2 vs irPI in a Scheffe post hoc test following an ANOVA with genotype as the factor, F2,60=4.142, p=0.021) (Figure 9). These data demonstrate that herbivore-induced GLV emissions function as indirect defenses by increasing predation of Manduca spp. larvae twofold, resulting in a twofold increase in bud and flower production for N. attenuata in its native habitat.
To ensure that our results were not biased by the use of wild Manduca spp. larvae, which comprised both M. sexta and M. quinquemaculata, we analyzed the growth (length over time) and instar change of larvae on plants in M4 by larval species. M. sexta and M. quinquemaculata did not differ in their growth or instar progression (N=11–13, repeated measures ANOVA for days 4–11, Wilks' Lambda for the interaction of day and species: F11,12=1.356, p=0.311). Because larvae of the two species cannot be distinguished before the third instar, we could not test whether mortality was equal for both species in the first three instars; however, because other collections of wild eggs around the same time as the collection for our experiment yielded a 1:1 ratio of species, and because our ratio of the species remained 1:1 after larvae reached the third instar, it is likely that mortality of the two species was equal prior to the third instar.
TPIs had a less consistent and, contrary to our expectations, negative effect on Manduca spp. predation (Figure 5); furthermore, there was no positive effect of TPIs on plant growth and reproduction (Figure 6, statistics Table 3) and only a marginal effect of TPIs on Manduca spp. growth under natural conditions (N=13–26 second instar larvae during M2, one-way ANOVAs with genotype as the factor, F3,77=2.792, p=0.046, all post hoc tests p>0.05, Figure 10; N=8 second instar larvae during M4, paired t-test between matched WT and irPI, p=0.052). We hypothesized that the reduced access to protein for larvae feeding on TPI-producing plants might nevertheless affect Manduca spp. behavior independently of larval size. Indeed, wild Manduca spp. larvae feeding on WT plants (infestation M4, Figure 4) reacted more sluggishly to experimental provocation than size-matched larvae on irPI plants: they were 75% less likely to attack when lifted off of the leaf (N=5 second-instar larvae matched for size, p=0.035 in paired t-test) (Figure 10, Videos 1 and 2).
We were careful not to harm wild larvae so that we could monitor their natural mortality and consequences for plant reproduction (Figure 9). To more accurately imitate Geocoris spp. attack, we developed an off-plant assay with larvae from the laboratory M. sexta strain feeding on detached leaves from field-grown plants, in which size-matched larvae were poked, pierced and lifted using an insect pin to mimic the Geocoris spp. beak (Figure 10, Videos 3 and 4). Similarly to the on-plant assay, larvae fed on WT leaves were 50% less likely to successfully attack the insect pin, either when initially poked, or poked and lifted with the pin (N=20 first-instar larvae matched for size, p<0.05 in paired t-tests) (Figure 10). We also monitored recovery post-trial and found that WT-fed larvae ceased to grow for at least 24 hr after simulated attack, while irPI-fed larvae continued to grow (p=0.016 in Student's t-test); mortality did not differ (p=0.527 in Fisher's exact test) (Figure 10).
Thus TPIs did not increase plant reproduction under attack from Manduca spp. in nature, but may support indirect defense by weakening the response of larvae to predator attack. The contradictory higher predation rates of Manduca spp. larvae from irPI than from WT plants (Figure 5) might reflect Geocoris spp.'s feeding preference, if irPI-fed larvae are more nutritious than WT-fed larvae (Kaplan and Thaler, 2011).
Our data demonstrate that herbivore-induced GLV emissions function as indirect defenses by increasing predation of Manduca spp. twofold, resulting in a twofold increase in bud and flower production for N. attenuata in its native habitat. In contrast, there was no positive effect of TPIs on plant growth and reproduction and no significant effect of TPIs on Manduca spp. growth under natural conditions; however, TPIs may support indirect defense by weakening the response of larvae to predator attack. Although this indicates that predation rates from irPI plants should be reduced, we observed a tendency towards higher predation rates from irPI than from WT plants; this could reflect Geocoris spp.'s preference if irPI-fed larvae are more nutritious than WT-fed larvae (Kaplan and Thaler, 2011).
The hemi-irLOX2 plants used in this study were created by crossing homozygous irPI and irLOX2 plants, but the irPI construct was not active in the hemizygous state (Figure 1). We continued to use this cross for its less severely reduced GLV production in comparison to homozygous irLOX2 plants (Figures 2 and 3), which likely permitted growth and reproduction comparable to irPI and WT in 2011 that was essential for plant matching prior to the final assays of Manduca spp. mortality and plant reproduction (M4, Figures 4 and 9). It is common molecular biology knowledge that functional RNAi constructs may be rendered ineffective as a result of insufficient gene dosage, for example, Travella et al. (2006) and references therein, which may occur when an RNAi construct is present in the hemizygous state (García-Pérez et al., 2004). The 35S promoter which drives the transcription of the RNAi construct may also be methylated: an epigenetic effect which can reduce the dose of RNAi in individual plants within a single transformed line (A Weinhold, unpublished data). This may have occurred in the irPI parent used for the creation of the hemi-irLOX2 line, although loss of activity of the irPI construct was not observed in the homozygous irPI line over the lifetime of plants in the field (Figure 1).
Although the production of viable offspring is the accepted definition of Darwinian fitness, we are not permitted to allow transgenic plants to disperse ripe seed in the field, and measures to prevent seed dispersal, such as bagging meristems, strongly affect production of buds and flowers and can also affect seed viability by increasing temperature, and decreasing respiration and photosynthesis of reproductive tissue and associated green tissue.
For field-grown N. attenuata plants, fewer than 5% of buds and flowers (in total) are aborted by healthy (not diseased) plants, and abortion seems always to be due to damage by insects (M C Schuman and I T Baldwin, personal observation, June 2010). Plants are self-compatible and more than 70% of seed set from plants in native populations results from fertilization via self-pollen (Sime and Baldwin, 2003). Thus numbers of buds and flowers correlate to lifetime seed capsule production, which in turn correlates to lifetime seed production, which has been used as a proxy measure of Darwinian fitness (Baldwin, 1998; van Loon et al., 2000; Hoballah and Turlings, 2001). The transgenic lines used do not vary in seed mass or their seedling viability under laboratory conditions.
During the 2011 experiment, we saw a large and reproducible difference in predation from GLV-emitting versus GLV-deficient plant genotypes, which was not observed in 2010 due to an absence of Geocoris spp. predators in that year. This difference in predation rate correlated to a difference in plant growth and reproduction which was also not observed in 2010. To rigorously test the consequences of GLV-mediated predation of Manduca spp. on plant reproduction, we selected triplets of WT, irPI and hemi-irLOX2 plants similar in size, previous reproductive output, apparent health, and prior damage to carry out Manduca spp. mortality and plant reproduction assays (M1 in 2010, M4 in 2011, Figure 4). We removed all reproductive meristems from matched plants in 2011 to allow us to follow plant reproduction over full Manduca spp. larval development without incurring ripe transgenic seed capsules. In 2010 (and during infestation M3 in 2011, Figure 4), we had removed and counted flowers regularly to track reproduction while avoiding ripe seed; this did not cause a difference in reproduction among genotypes (Figure 6), but we elected to avoid flower removal during infestation M4 by removing reproductive meristems prior to the beginning of the assay.
The hemi-irLOX2 plants chosen in 2011 had produced more flowers than WT – but not more than irPI—prior to the start of infestation M4 (Figures 4 and 8). This did not correspond to more cuts on average for hemi-irLOX2 when removing reproductive meristems: meristems were cut at the bases of inflorescences which contained mostly buds, and the number of these did not differ for the plants chosen, nor did the number of side branches (Figure 8) which bore most reproductive meristems. Therefore, in the absence of additional effects during infestation M4, the reproduction of the matched hemi-irLOX2 plants should have been similar to that of WT and irPI.
By indicating the long-sought indirect defensive function of HIPVs, these data set the stage for the use of HIPVs as part of integrated pest management strategies (IPM), which rely in part on recruiting biological control agents to reduce pesticide use (Horne and Page, 2008). These agents are usually naturally occurring generalist parasitoids and predators, such as Geocoris spp. (Eubanks and Denno, 1999, 2000; Allison and Hare, 2009; Allmann and Baldwin, 2010). HIPVs are produced by genotypes of most, if not all crop plants and IPM would benefit from selective breeding or engineering of HIPV emission (Kos et al., 2009) rather than relying on alternatives such as controlled release dispensers, which have mixed success and require large amounts of synthetic HIPVs (Kaplan, 2012). PIs may be employed to enhance the efficiency of indirect defense, especially combined with toxins like Bt that directly target herbivores and are safe for biological control agents. With growing concerns about field-evolved Bt resistance (Liu et al., 2010), indirect defenses promise an effective 'first line of defense' against agricultural pests, to which not even specialist herbivores are likely to rapidly evolve resistance.
Seed germination, glasshouse growth conditions, and the Agrobacterium tumefaciens (strain LBA 4404)–mediated transformation procedure have been described previously (Krügel et al., 2002). Seeds of the 31st generation of the inbred 'UT' line of Nicotiana attenuata (Torr. ex S. Wats.) were used as the wild-type plant in all experiments. For the field experiment, seedlings were transferred to 50 mm peat pellets (Jiffy) 15 days after germination and gradually hardened to the environmental conditions of high sunlight and low relative humidity over 10 days. Small, adapted, size-matched rosette-stage plants were transplanted into a field plot in a native habitat in Utah and watered thoroughly once at planting and as needed over the first 2 weeks until roots were established; all plants received the same watering regime in each year. WT, irPI, irLOX2 and hemi-irLOX2 plants were arranged in quadruplets (N=40–50) of one plant per genotype, with individuals 0.5 m apart, a distance sufficient to allow predators and herbivores to distinguish volatiles from neighboring plants (Kessler and Baldwin, 2001). Quadruplets were arranged so that no two adjacent plants were of the same genotype (Figure 4). In 2010, the field plot was a first-year plot located at latitude 37.141, longitude 114.027; in 2011, plants were planted at a second, older field site across a river from the first, located at latitude 37.146, longitude 114.020. Field plantations were conducted under APHIS permission numbers 06-242-3r-a3 (2010 and 2011) and 10-349-102r (2011).
We used previously characterized, homozygous, inverted-repeat (ir) RNAi transformed lines of the second transformed generation (T2) to silence GLV biosynthesis: irLOX2 line number A-04-52-2 (Allmann et al., 2010), and TPI activity: irPI line number A-04-186-1 (Steppuhn and Baldwin, 2007). Vector construction and the pSOL3 plasmid have been described previously (Bubner et al., 2006). A cross was created between irLOX2 and irPI homozygous lines; however, the hemizygous irPI construct did not silence TPI activity or transcripts, and these plants therefor served as vector controls for comparison with irPI and had slightly greater residual GLV production than irLOX2 (see 'Results'). They are thus referred to as hemizygous (hemi-)irLOX2 plants.
Wild Manduca spp. eggs were collected for field assays when available from natural ovipositions. M. sexta and M. quinquemaculata (hereafter Manduca spp.) were both ovipositing at the time experiments were conducted; the species of larvae was identified at the third instar and recorded (earlier instars of these two species cannot be distinguished morphologically). M. sexta and M. quinquemaculata oral secretions (OS) are highly similar in their composition (Halitschke et al., 2001) and elicit similar volatiles (Halitschke et al., 2001; Kessler and Baldwin, 2001) and defense genes (Schittko et al., 2001) in N. attenuata. Eggs from laboratory-reared M. sexta, kindly provided by Dr. Carol Miles at SUNY Binghampton, were used in the field when wild Manduca spp. eggs were not sufficiently abundant. Eggs were allowed to hatch in well-aerated boxes on fresh N. attenuata leaf tissue over a moistened paper towel. M. sexta larvae used to elicit glasshouse-grown plants, or to collect oral secretions (OS) for plant treatments, were taken from an in-house colony at the Max Planck Institute for Chemical Ecology in Jena, Germany.
Because GLVs influence Manduca spp. oviposition (De Moraes et al., 2001; Kessler and Baldwin, 2001; Fraser et al., 2003), and the timing and extent of Manduca spp. oviposition varies from year to year, we created even, synchronous oviposition events by infesting plants with Manduca spp. larvae, either from a lab-reared culture or from wild collections (see Manduca spp. eggs and larvae). Larvae used for plant infestations were placed as neonates on a rosette or lower stem leaf at a standardized position for each assay, and monitored mornings and evenings, during times outside of the main period of Geocoris spp. activity that occurs at midday. Plants in field experiments were either infested with Manduca spp. larvae as described above, or left uninfested (control). There were four infestations over both years of the experiment, denoted M1-M4 in Figure 4.
For measuring headspace GLVs in the field and for glasshouse assays, plants were treated with wounding and M. sexta OS (W+OS) as a standardized method to mimic Manduca spp. feeding. Pure OS collected from fourth to fifth instar M. sexta larvae from the Jena colony fed on WT plants was diluted 1:5 with distilled water before use; even 1000-fold diluted OS is still sufficient to cause most OS-elicited responses (Schittko et al., 2000). For field-grown plants, a similar, mature, non-senescent leaf was chosen from each plant; for glasshouse-grown plants, the two adjacent older leaves (nodes +1, +2) to the leaf undergoing a source-sink transition (node 0) on rosette-stage plants were used for PI and LOX2 transcript quantification, and the +2 node of a separate set of bolting plants was used for measuring headspace volatiles. The leaf chosen for treatment was wounded by using a fabric pattern wheel run over the adaxial surface to make six rows of holes in the lamina, three rows on either side of the midvein. 20 µL of 1:5 diluted OS were deposited on the adaxial surface and gently rubbed over the holes with a gloved finger. Control plants were left untreated.
For field-grown plants and glasshouse-grown M. sexta-fed plants, a similar, mature, non-senescent systemic (undamaged) leaf was chosen from each plant; for glasshouse-grown plants used to measure PI and LOX2 transcripts, the leaves at nodes +1 and +2 (treated leaf positions) were harvested. Leaves were cut at the petiole and wrapped in a double layer of aluminum foil. In the field, harvested leaves were immediately frozen on dry ice insulated with ice packs frozen at −20°C; samples were stored at −20°C until transport to Jena on dry ice, where they were kept at −80°C until analysis. Leaves harvested from glasshouse-grown plants were flash-frozen in liquid nitrogen and kept at −80°C until analysis. All sample processing was carried out over liquid nitrogen until the addition of the extraction solvents. Prior to analysis, entire leaves were ground with a mortar and pestle and transferred to a 2 mL microcentrifuge tube for storage. For specific measurements, aliquots were weighed into microcentrifuge tubes containing two steel balls and finely ground in a GenoGrinder (SPEX Certi Prep) prior to extraction.
TPI activity was quantified in 100 mg of tissue from systemic leaves on Manduca spp.-infested plants using a radial diffusion assay as previously described (van Dam et al., 2001).
Leaf samples were from control plants or plants treated with W+OS. Treated leaf positions were harvested at the peak of transcript accumulation for PI, 12 hr (Wu et al., 2006) and LOX2, 14 hr (Allmann et al., 2010). Total RNA was extracted from leaves using the TRIzol reagent (Invitrogen), and a 0.5 μg aliquot of total RNA of each sample was reverse-transcribed using oligo(dT)18 and RevertAid H Minus reverse transcriptase (Fermentas) following the manufacturer's instructions. Quantitative real-time PCR (qPCR) was performed with a Mx3005P Multiplex qPCR system (Stratagene) and the qPCR Core kit for SYBR Green I (Eurogentec). Transcripts were quantified using external standard curves for each gene. Elongation factor 1A (EF1A) transcript abundance in each sample was used to normalize total cDNA concentration variations. Samples of RNA used to make cDNA were pooled to the same dilution as in cDNA samples and run alongside cDNA in all qPCRs to control for gDNA contamination; no contamination was detected. The sequences of primers used for qPCR (Kallenbach et al., 2010; Fragoso et al., 2011) are provided in Table 4.
To assess qualitatively the GLV pools in leaf tissue from field-grown plants, and to determine appropriate amounts of leaf tissue and internal standard (IS) for GLV extraction, we extracted pooled samples from leaves collected June 6, 2011, from M. sexta-infested plants during infestation M3 (Figure 4). Each sample was pooled from all leaves collected from one genotype. Hexane (300 µL) was added to 100 mg tissue spiked with 3 µg tetralin as an internal standard (IS) and incubated by rotating at RT overnight. Samples were allowed to settle and 100 µL of water- and tissue-free hexane was transferred to a GC vial containing a 250 µL microinsert. Individual analytes were analyzed by a Varian CP-3800 GC-Saturn 4000 ion trap MS connected to a ZB5 column (30 m×0.25 mm i.d., 0.25 μm film thickness; Phenomenex). 1 μL of samples was injected by a CP-8400 autoinjector (Varian) onto the column with a 1:10 split ratio; the injector was returned to a 1:70 split ratio from 2 min after injection through the end of each run. The GC was programmed as follows: injector held at 250°C, initial column temperature at 40°C held for 5 min, then ramped at 5°C/min to 185°C and finally at 30°C/min to 300°C, held for 0.17 min. Helium carrier gas was used and the column flow set to 1 mL/min. Compounds eluted from the GC column were transferred to the MS for analysis. The MS was programmed as follows: transfer line at 250°C, trap temperature 110°C, manifold temperature 50°C, source heater 200°C and scan range from 40 to 399 m/z at 1.33 spectra per second as previously described (Schuman et al., 2009). The identification of compounds was conducted by GC retention time compared to pure standards and mass spectra compared to standards and mass spectra databases, Wiley version 6 (Wiley) and NIST (National Institute of Standards and Technology) spectral libraries.
For the quantification of GLV pools in leaf tissue from field-grown plants, the hexane extraction protocol was adjusted based on GC-MS results from pooled samples (described above), and a GC-FID with a wax column was used for the quantitative analysis of extracts. Hexane (300 µL) were added to 50 mg tissue (N=10) spiked with 15 µg (Z)-hex-3-enyl acetate, a GLV not found in GC-MS samples, as an IS. The extraction proceeded as described above. Analytes were separated by Varian CP-3800 GC-FID connected to a ZB-Wax column (30 m×0.25 mm i.d., 0.25 μm film thickness; Phenomenex). 1 μL of samples was injected by a CP-8400 autoinjector (Varian) onto the column in a splitless mode; the injector was returned to a 1:70 split ratio 2 min after injection through the end of each run. The GC was programmed as follows: injector held at 230°C, initial column temperature at 40°C held for 7 min, then ramped at 5°C/min to 115°C and finally at 30°C/min to 250°C, held for 0.5 min. Helium carrier gas was used and the column flow set to 1 mL/min. Compounds eluted from the GC column were transferred to a Varian FID set at 250°C for analysis (airflow 300 mL/min, hydrogen 30 mL/min, nitrogen make-up gas 5 mL/min). Individual volatile compound peaks were quantified by peak areas using MS Work Station Method Builder and Batch Report software (Varian) and normalized to the peak area of the IS (Z)-hex-3-enyl acetate in each sample. Peak identification and quantification was done by comparison to standard curves of pure compounds in hexane. Compounds present in quantifiable amounts were (Z)-hex-3-en-1-ol, (E)-hex-2-enal and the IS (Z)-hex-3-enyl acetate.
For measurement of GLVs in the headspace of field-grown plants, intact leaves were harvested (N=3) and kept fresh by placing the petioles in microcentrifuge tubes filled with water. Immediately before each measurement, one leaf was treated with W+OS, and a 1 cm2 disc was stamped out and placed in a 4 mL GC vial. After 15 min, the headspace in the vial was measured with a ZNose 4200 portable gas chromatograph with a 1 m DB5 column (Electronic Sensor Technology, Newbury Park, CA, USA) by inserting the ZNose inlet needle through the septum of the GC vial into the headspace. The program was as follows: valve set at 165°C, inlet at 200°C, trap at 250°C; 30 s sampling time, column ramped from 30°C to 190°C at 4°C/s, data collection for 20 s. Genotypes were analyzed in an alternating order within each replicate: first replicate 1 of all genotypes, then replicate 2, then replicate 3. Retention times of GLV aldehydes and alcohols, the most abundant GLV headspace components, were determined using pure standards.
For the analysis of GLVs in the headspace of glasshouse-grown plants, the +2 leaf was enclosed immediately after W+OS elicitation in a food-quality 50 mL plastic container (Huhtamaki) with an activated charcoal filter attached to one side for incoming air, and connected to self-packed Poropak Q filters containing 20 mg of Poropak (Sigma-Aldrich) packed with silanized glass wool and Teflon tubing in the column bodies (ARS, Inc.) as previously described (Halitschke et al., 2000; Schuman et al., 2009). Ambient air was pulled by vacuum pump for 3 hr through an activated charcoal filter, over the leaf in the trapping container, and through a Poropak Q filter connected by PVC tubing (Rotabilo) to a custom-made valve manifold, as previously described (Schuman et al., 2009); the manifold was adjusted such that flow rates through traps were ca. 300 mL/min. After trapping, sampled leaves were excised at the base of the petiole, scanned, and the leaf area was measured in comparison to a 1 cm2 standard (SigmaScan 5.0; Systat Software Inc.) for normalization of volatile emission to cm2 leaf area. Poropak Q filters were wrapped in aluminum foil and stored at −20°C until elution of volatiles with 250 μL dichloromethane (Sigma-Aldrich).
Immediately prior to elution, each filter was spiked with 320 ng of tetralin internal standard (IS) in hexane (Sigma-Aldrich). Filters were eluted into a GC vial containing a 250 μL glass insert. Samples were analyzed by a CP-3800 GC Varian Saturn 2000 ion trap MS (Varian) connected to a polar ZB-wax column (30 m×0.25 mm i.d., 0.25 μm film thickness; Phenomenex). 1 μL of samples was injected by a CP-8200 autoinjector (Varian) onto the column in a splitless mode; the injector was returned to a 1:70 split ratio from 2 min after injection through the end of each run. The GC was programmed as follows: injector held at 230°C, initial column temperature at 40°C held for 3 min, then ramped at 5°C/min to 180°C and finally at 10°C/min to 240°C, held for 1 min. Helium carrier gas was used and the column flow set to 1 mL/min. Eluted compounds from the GC column were transferred to the MS for analysis. The MS was programmed as follows: transfer line at 230°C, trap temperature 150°C, manifold temperature 80°C and scan range from 40 to 399 m/z at 1.33 spectra per second as previously described (Schuman et al., 2009). Individual volatile compound peaks were quantified by peak areas of two specific and abundant ion traces per compound using MS Work Station Data Analysis software (Varian) and normalized by the 104+132 ion trace peak area of the IS (tetralin) in each sample. The identification of compounds was conducted by GC retention time compared to pure standards and mass spectra compared to standards and mass spectra databases, Wiley version 6 (Wiley) and NIST (National Institute of Standards and Technology) spectral libraries. In 3 hr headspace samples we detected (Z)-hex-3-en-1-ol, (Z)-hex-3-en-1-ol, (E)-hex-2-en-1-ol (forms from (E)-hex-2-enal on filters over trapping periods longer than 20 min), (Z)-hex-3-enyl acetate, (Z)-hex-3-enyl butanoate, (Z)-hex-3-enyl isobutyrate, and (Z)-hex-3-enyl propanoate.
The collection of (E)-α-bergamotene from the headspace of glasshouse-grown plants and its extraction from Poropak Q filters was carried out as for GLVs, except that (E)-α-bergamotene was collected 24–32 hr after W+OS treatment of the leaf. Eluted samples were analyzed by an HP 6890 GC-5973 quadropole MS (Hewlett-Packard) connected to a nonpolar DB-5ms column (30 m×0.25 mm i.d., 0.25 μm film thickness; Agilent). 1 μL of samples was injected by a HP 7683 autoinjector (Hewlett-Packard) onto column in a splitless mode; the injector was purged at 50 mL/min 1.5 min after injection and switched to gas saver mode (20 mL/min) from 10 min through the end of each run. The GC was programmed as follows: injector held at 230°C, initial column temperature at 40°C held for 2 min, then ramped at 5°C/min to 165°C and finally at 60°C/min to 300°C, held for 2 min. Helium carrier gas was used and the column flow set to 2 mL/min. Eluted compounds from GC column were transferred to the MS for analysis. The MS was programmed as follows: source at 230°C, quad temperature 150°C, and scan range from 33 to 350 m/z at 4.49 spectra per second. (E)-α-Bergamotene was quantified by peak area using the ion trace 119 m/z in Chemstation software (Agilent) and normalized by the 104 ion trace peak area of the IS (tetralin) in each sample. The identification of (E)-α-Bergamotene and tetralin IS was conducted by GC retention time and mass spectra compared to mass spectra of known standards as previously described (Schuman et al., 2009).
One or two larvae were placed on plants at a time for each assay, depending on the number available, and were equally distributed among plants as described under ‘Manduca spp. infestation and W+OS treatment of plants'. However, for infestation M3 (Figure 4), we staggered the infestation of different plant genotypes to accommodate differences in plant growth: WT and irPI plants were initially larger and therefore went into the field on average earlier than irLOX2 and hemi-irLOX2 plants, so that all plants were planted at a similar size, which is important for even establishment. We therefore re-infested WT and irPI plants earlier after M1, to allow irLOX2 and hemi-irLOX2 plants to catch up in their growth to WT and irPI before re-infestation. However, we then left M. sexta larvae on irLOX2 and hemi-irLOX2 as long as on WT and irPI, and we used a combination of Geocoris spp. counts and additional predation assays to make sure that differences in Geocoris spp. predation were not due to this staggering of infestation (see 'Results: Geocoris spp. preferentially predate from GLV-perfumed or -emitting plants').
Manduca spp. behavior, predation, and growth assays were conducted with first- and second-instar larvae, except infestations M1 2010 and M4 in 2011, in which larvae were reared from the first through fifth instars on plants; and egg predation assays, in which M. sexta eggs were used.
Larvae used in the off-plant mock predation assays were hatched on the appropriate N. attenuata genotype (WT or irPI) and hatching was monitored three times per day (morning, noon, evening) so that the mock predation assay could be timed to 48 hr after larvae hatched. A protocol of the mock predation assays is given in Figure 10, and Videos 1–4 depict on-plant (1 and 2) and off-plant (3 and 4) behavioral assays. Larvae for off-plant mock predation assays were kept in aerated plastic boxes on cut leaves over moist paper towels. Leaves were refreshed twice daily and were kept fresh by placing the petioles in water in 1.5 mL microcentrifuge tubes which were closed around the petiole with Parafilm (Pechiney Plastic Packaging Company). Larval growth was measured as increases in body length (in millimeters) using calipers or a small, flexible, transparent plastic ruler.
Predation rates were recorded for larvae placed on plants as described above, or for two eggs per plant fixed with droplets of α-cellulose glue (Kessler and Baldwin, 2001) to the underside of a rosette or lower stem leaf at a standardized position. For egg predation assays, a wild Manduca spp. larva was enclosed on a nearby leaf to ensure continual GLV emission: a clip cage was closed around the larva to make it inaccessible to Geocoris spp. predators. Predation was monitored mornings and evenings. Larvae were considered to be predated when either the larva was missing over multiple days, but clear Manduca spp. feeding damage was present, or when the predated larval carcass was found (Figure 5). Mortality was defined as the total number of missing larvae. Eggs were considered predated when the eggshell was empty but intact except for a small hole which characterizes the typical damage caused by Geocoris spp. feeding; eggs occasionally collapse during Geocoris spp. predation, but collapsed eggs were not counted unless the eggs were mostly or fully empty and with a visible hole (Figure 5).
During infestation M2, GLVs were added back to irLOX2 and hemi-irLOX2 headspaces by placing a cotton swab adjacent to the M. sexta-infested leaf and adding ca. 20 µL of lanolin paste, measured with a seed spoon, containing a mix of pure GLVs representative of the M. sexta-fed headspace and dissolved in hexane (Table 1) (Allmann and Baldwin, 2010) to the cotton swab. Cotton swabs bearing ca. 20 µL of lanolin paste with hexane as a control were placed next to M. sexta-infested leaves of WT and irPI plants. Lanolin pastes were regularly refreshed by adding 20 µL in the early afternoon and in the morning. Placing GLVs next to, rather than on the leaf ensured that the supplemented headspace would not be altered by plant metabolism, and that we could terminate the supplementation by removing the cotton swabs.
Field plots were monitored daily for Geocoris spp. presence during the experiments in 2010 and 2011; both G. pallens and G. punctipes were present in 2011, but most individuals observed on and around plants were G. pallens. Soon after the first Geocoris spp. sightings in May 2011 (before the first infestation, M2), Geocoris spp. populations in the immediate vicinity of experimental plants were monitored every 2–3 days by counting individuals. Counts were conducted during the main period of Geocoris spp. activity in the early afternoon, by at least two observers in parallel, in order to complete the count around all Manduca spp.-infested and control plants within 20–30 min. Each observer proceeded by looking at a focal plant and its immediate vicinity for 15 s and then quickly inspecting the rosette leaves; all Geocoris spp. adults and nymphs seen on, under, or within 5 cm around the rosette of the plant during this time were counted. Observers moved in synchrony with each other from one end of the field plot to the other, in this way counting predators around plants which had not yet been disturbed.
Plant size (rosette diameter, stem length and branching) was monitored at the end of infestation M1 in 2010 and from the beginning of infestation M2 in 2011 (Figure 4): rosette diameter was measured as the maximum diameter found by gently laying a ruler over the rosette; stem length was measured from the base of the stem to the tip of the apical inflorescence by placing a ruler beside the stem; and all side branches 5 cm or longer were counted. Reproductive output was monitored by counting the number of closed flowers removed every 2–3 days (before they opened) from the beginning of flowering, and by counting numbers of closed flowers and buds 2 mm or larger at the end of infestation M1 in 2010, and during all infestations in 2011. All growth and reproduction data were analyzed for differences in control versus M. sexta-infested plants within each genotype (statistics Table 3). Because size-matched plants had been planted over one week in 2011, growth and reproduction data from plants in 2011 were organized by the number of days since planting for comparison between genotypes (Figure 6).
Flowers were removed and counted periodically over the first 10 days of infestation M1 and during infestation M3 (Figures 4 and 6, statistics Table 3), in order to track plant reproduction while avoiding ripe seed capsules: the distribution of ripe seed is not permitted for genetically modified plants. For infestation M4 in 2011 (Figure 4), instead of regularly removing flowers, we removed all reproductive meristems by cutting inflorescences, which contained mostly buds, at their base, so that we would be able to follow a new set of reproductive meristems through to seed set without incurring ripe seed. Because plants were matched prior to M4 and had the same number of buds and of side branches (which usually terminate in inflorescences) (Figure 8, see 'Discussion'), all plants were similarly affected by the removal of reproductive meristems.
Photographs were taken of entire plants and M. sexta-damaged leaves during infestations M2 and M3 in 2011. Damage caused by M. sexta larvae was rated from photographs by an independent observer with no knowledge of plant identity. Total percent canopy damage due to M. sexta was rated as 1, 2, 3, or 4 using the damage index in Figure 7.
We monitored herbivore attack to determine whether GLV-silenced plants suffered different amounts of herbivore damage, which could influence fitness measurements. The naturally occurring herbivore community on plants in 2010 and 2011 comprised mirids (Tupiocoris notatus) and noctuid larvae; in 2011 grasshoppers (Trimerotropis spp.) and flea beetles (Epitrix spp.) were also present. Total canopy damage due to herbivores occurring naturally on the field plot was quantified prior to the infestations in 2010 and 2011 and again during infestation M3 in 2011. Damage was calculated by identifying damage from specific herbivores according to their characteristic feeding patterns, counting the number of leaves per plant (small leaves were counted as 1/5 to 1/2 of a leaf based on leaf area and large leaves were counted as 1 leaf), estimating the total percentage of leaf area damage due to each herbivore, and dividing the total leaf area damage from each herbivore by the total number of leaves. Leaf area damage was estimated in categories of 1%, 5%, 10%, 15%, and so on, in steps of 5%. All such damage estimates were made by MCS or KB, who first practiced quantifying damage together until they consistently arrived at the same numbers.
As part of matching plants prior to infestation M4 in 2011, plant health was rated on a scale of 1 (dead) to 5 (healthy) using the index in Figure 7.
Fisher's exact tests were conducted using a macro (J H Macdonald, http://udel.edu/~mcdonald/statfishers.html) for Excel (Microsoft). All other statistical analyses were conducted with SPSS 17.0 (IBM). Count data were analyzed either by Fisher's exact tests (independent values) or by Friedman tests (repeated measures). Levene's test for homogeneity of variance was performed prior to all t-tests and ANOVAs and when necessary, data were log2 transformed (volatile and transcript data), square root transformed (count data) or arcsin transformed (herbivore damage data) to meet requirements for homogeneity of variance. Parametric data were compared using ANOVAs, MANOVAs, or repeated-measure ANOVAs followed by Scheffe post hoc tests. If variance was not homogeneous following transformation, data were compared using Kruskal-Wallis tests (for multiple comparisons) or Mann-Whitney U-tests (for two-way comparisons) and Bonferroni p-value corrections were used to correct for nonparametric multiple comparisons. For Kruskal-Wallis tests and Mann-Whitney U-tests, a Monte Carlo algorithm was used with 10,000 permutations and a 95% confidence level.
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Detlef WeigelReviewing Editor; Max Planck Institute for Developmental Biology, Germany
eLife posts the editorial decision letter and author response on a selection of the published articles (subject to the approval of the authors). An edited version of the letter sent to the authors after peer review is shown, indicating the substantive concerns or comments; minor concerns are not usually shown. Reviewers have the opportunity to discuss the decision before the letter is sent (see review process). Similarly, the author response typically shows only responses to the major concerns raised by the reviewers.
Your manuscript “Herbivory-induced volatiles function as defenses increasing plant fitness in nature” has been reviewed. The following individual(s) responsible for the peer review of your submission want(s) their identity to be known: Detlef Weigel (reviewing editor); Joerg Bohlmann (reviewer).
We are happy to tell you that a revised manuscript shall be acceptable for eLife. Here are the comments:
The hypothesis outlined in the title of this paper, that indirect defences in the form of herbivory-induced volatiles increase plant fitness, is being continuously discussed in the literature, without there being much definitive evidence for this phenomenon occurring in nature. It is a difficult hypothesis to test, but the authors of this work make a big step toward providing an answer.
In field studies over two seasons (with both wild and lab-reared predators) complemented with lab experiments, the authors examined how emission of volatile organic compounds (VOCs) and a protease inhibitor (TPI) that reduces digestibility of plant tissue affect herbivore growth and plant fitness, as measured by flower buds and seed set in tobacco. The experimental approach was to reduce VOCs by silencing the LOX2 gene, and TPI activity by silencing the PI gene.
The authors clearly show that plants that emit less VOCs attract fewer Geocoris predators to Manduca herbivores (Fig. 2), and that Manduca mortality is reduced in the presence of Geocoris (Fig. 3A). The result is that fewer flowers and flower buds are produced, but only in the presence of Geocoris (Fig. 3B).
The authors are to be commended for reporting a comprehensive set of measurements, including ones that are not easily explained or fit the hypotheses examined. This makes unfortunately in several places for difficult reading. In addition, the paper is extremely densely written and difficult to follow for those unfamiliar with the research program of the authors. To make the content of the work more accessible, the paper should be presented with separate sections for introduction, results, and discussion, and subsections for the results. In addition, the supplementary figures as well as the supplementary narrative should be integrated into the main text, and the data should be better and more consistently presented in the figures. For example, the colour code for different genotypes in Fig. S1-3 and 6A,B should also be applied in all other figures.
Some essential information is only mentioned in passing, e.g., that homozygous irLOX2 lines “… did not suffer reduced growth or reproduction from Manduca sexta feeding … and that they were too small …”. This must be explained, and better justification must be provided for focussing on the hemizygous lines, especially because it is not entirely clear how the effects on VOCs compare between hemi- and homozygous plants.
Other important points: (i) The statement in the Introduction (beginning “Although GLVs are released upon mechanical damage…”) must be at least changed to: “… the oral secretions of Manduca convert 3-(Z)-GLVs to the 2-(E)-structures, …” (This is because this is a rearrangement, not an isomerisation). (ii) The authors should consider whether the experiments in Fig. 4 regarding the effects of TPI on M. sexta behaviour, though interesting, distract from the rest of the work. Perhaps they could be omitted from this manuscript?
A final remark: it is a pity that, because of global attitudes to genetically modified plants, the authors could not evaluate ripe seeds.https://doi.org/10.7554/eLife.00007.021
Reviewer comments are in italics.
The authors are to be commended for reporting a comprehensive set of measurements, including ones that are not easily explained or fit the hypotheses examined. This makes unfortunately in several places for difficult reading. In addition, the paper is extremely densely written and difficult to follow for those unfamiliar with the research program of the authors. To make the content of the work more accessible, the paper should be presented with separate sections for introduction, results, and discussion, and subsections for the results. In addition, the supplementary figures as well as the supplementary narrative should be integrated into the main text, and the data should be better and more consistently presented in the figures. For example, the colour code for different genotypes in Fig. S1-3 and 6A,B should also be applied in all other figures.
We have now organized the manuscript into an introduction, Materials and Methods, results, and discussion, with subsections in the Methods, Results, and Discussion sections following the order of the figures and tables. In particular, we have expanded the explanation of the data behind new Figures 8 and 9 (infestations M1 and M4).
We have also implemented consistent color codes for the genotypes, and consistent pattern codes for control vs Manduca spp.-infested or W+OS-treated plants, and a more consistent format for the figures. We have also merged some figures which were formerly separate but described the same results or sets of assays.
A note: in the interest of clarity, we now include reports of statistical analyses in the text and not only in figure captions or tables. Perhaps it could be considered to convert these in-text statistical reports to mouse-over hypertext in the online version of the paper, since the long parantheticals interrupt the flow of the text.
Some essential information is only mentioned in passing, e.g., that homozygous irLOX2 lines “… did not suffer reduced growth or reproduction from Manduca sexta feeding … and that they were too small …”. This must be explained, and better justification must be provided for focussing on the hemizygous lines, especially because it is not entirely clear how the effects on VOCs compare between hemi- and homozygous plants (see minor comments below).
We have tried to clarify our description of the GLV pools and emissions from the irLOX2 and hemi-irLOX2 plants. It is clearly stated in the Materials and Methods and in the Results that the hemi-irLOX2 plants contain an inactive irPI construct, and the possible explanations for this construct's inactivity are discussed in a new section of the discussion, “WT levels of TPIs in hemi-irLOX2 plants are likely due to gene dosage effects”.
Other important points: (i) The statement in the Introduction (beginning “Although GLVs are released upon mechanical damage…”) must be at least changed to: “… the oral secretions of Manduca convert 3-(Z)-GLVs to the 2-(E)-structures, …” (This is because this is a rearrangement, not an isomerisation).
We have changed this sentence to “Although GLVs are released upon mechanical damage, the oral secretions (OS) of M. sexta convert 3-(Z)-GLVs to the 2-(E)-structures, resulting in greater Geocoris spp. predation than the damage-induced (Z):(E) ratio”.
(ii) The authors should consider whether the experiments in Fig. 4 regarding the effects of TPI on M. sexta behaviour, though interesting, distract from the rest of the work. Perhaps they could be omitted from this manuscript?
We recognize that this is a long, complex, and data-heavy manuscript. However, we feel that the behavior data is essential to the story, because it is the only effect we found of TPIs, and it is a novel effect which is highly relevant for the efficiency of indirect defense. Both because of the experimental designs presented in the paper, and because of the implications of these results, we feel they belong as part of this story. Also, if these data were not included, we would have to re-analyze all experiments without the irPI line, which we feel is artificial. The removal of these data would only save one figure and 3.5 paragraphs of text.
A final remark: it is a pity that, because of global attitudes to genetically modified plants, the authors could not evaluate ripe seeds.
We appreciate the reviewers' sympathy on this point!https://doi.org/10.7554/eLife.00007.022
- Meredith C Schuman
- Kathleen Barthel
- Ian Baldwin
The funder had no role in study design, data collection and interpretation, or the decision to submit the work for publication.
We thank S Allmann for conducting egg predation assays in 2010; C Diezel, M Erb, M Kallenbach, D Kessler, D Marciniak, M Stanton, and A Steppke for help with field work; S Weigl for rating M. sexta damage levels; J Gershenzon for the use of the HP GC-MS; M Erb, J Gershenzon, D Heckel, M Kallenbach, A Kessler, A Steppke, and A Weinhold for comments on the manuscript; Brigham Young University for the use of their Lytle Preserve field station; and APHIS for constructive regulatory oversight.
- Detlef Weigel, Max Planck Institute for Developmental Biology, Germany
- Received: May 7, 2012
- Accepted: July 11, 2012
- Version of Record published: October 15, 2012 (version 1)
© 2012, Schuman 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.
We investigated early vegetative growth of natural Arabidopsis thaliana accessions in cold, nonfreezing temperatures, similar to temperatures these plants naturally encounter in fall at northern latitudes. We found that accessions from northern latitudes produced larger seedlings than accessions from southern latitudes, partly as a result of larger seed size. However, their subsequent vegetative growth when exposed to colder temperatures was slower. The difference was too large to be explained by random population differentiation, and is thus suggestive of local adaptation, a notion that is further supported by substantial transcriptome and metabolome changes in northern accessions. We hypothesize that the reduced growth of northern accessions is an adaptive response and a consequence of reallocating resources toward cold acclimation and winter survival.
Root exudates are thought to play an important role in plant-microbial interactions. In return for nutrition, soil bacteria can increase the bioavailability of soil nutrients. However, root exudates typically decrease in situations such as drought, calling into question the efficacy of solvation and bacteria-dependent mineral uptake in such stress. Here we tested the hypothesis of exudate-driven microbial priming on Cupressus saplings grown in forest soil in custom-made rhizotron boxes. A 1-month imposed drought and concomitant inoculations with a mix of Bacillus subtilis and Pseudomonas stutzeri, bacteria species isolated from the forest soil, were applied using factorial design. Direct bacteria counts and visualization by confocal microscopy showed that both bacteria associated with Cupressus Interestingly, root exudation rates increased 2.3-fold with bacteria under drought, as well as irrigation. Forty four metabolites in exudates were significantly different in concentration between irrigated and drought trees, including phenolic acid compounds and quinate. When adding these metabolites as carbon and nitrogen sources to bacterial cultures of both bacterial species, 8 of 9 metabolites stimulated bacterial growth. Importantly, soil phosphorous bioavailability was maintained only in inoculated trees, mitigating drought-induced decrease in leaf phosphorus and iron. Our observations of increased root exudation rate when drought and inoculation regimes were combined, support the idea of root recruitment of beneficial bacteria, especially under water stress.