Summary
This paper reports that even specific targeted forms of pest resistance in plants can have non-target effects, and may not always be compatible with biological control for integrated pest management.
Key words: Biological control, host plant resistance, insect resistance, integrated pest management, Mi-1, Mi-1.2, mesophyll feeding, natural enemy, plant defence, R gene, xylem feeding.
Abstract
Mi-1.2 is a single dominant gene in tomato that confers race-specific resistance against certain phloem-feeding herbivores including aphids, whiteflies, psyllids, and root-knot nematodes. Few prior studies have considered the potential non-target effects of race-specific resistance genes (R genes), and this paper evaluates the compatibility of Mi-mediated resistance in tomato with a beneficial zoophytophagous predator, Orius insidiosus (Say). In addition to preying on aphids and other pests, this piercing–sucking insect also feeds from the xylem, epidermis, and/or mesophyll, and oviposits within plant tissues. Comparison of O. insidiosus confined to isogenic tomato plants with and without Mi-1.2 revealed that immatures of O. insidiosus had lower survival on resistant plants even when the immatures were provisioned with prey that did not feed on the host plant. Molecular gut content analysis confirmed that adults and immatures of O. insidiosus feed on both resistant (Mi-1.2+) and susceptible (Mi-1.2–) genotypes, and bioassays suggest that resistance does not affect oviposition rates, plant sampling, or prey acceptance by O. insidiosus adults. These results demonstrate a direct negative impact of R-gene-mediated host plant resistance on a non-target beneficial species, and reveal that Mi-mediated resistance can impact organisms that do not feed on phloem sap. Through laser capture microdissection and RT-PCR, Mi-1.2 transcripts were detected in the epidermis and mesophyll as well as the phloem of tomato plants, consistent with our observations that Mi-mediated resistance is active outside the phloem. These results suggest that the mode of action and potential ecological impacts of Mi-mediated resistance are broader than previously assumed.
Introduction
Although insect-resistant crop varieties and biological control agents are both important components of integrated pest management, they are not always fully compatible, because many of the resistance mechanisms that protect plants from herbivorous insects may also deter beneficial predatory insects. For example, structural defences such as trichomes, epidermal thickness, and waxy surfaces can impede prey-finding by predators (Obrycki, 1986; Eigenbrode, 2001; Kennedy, 2003), and certain secondary metabolites that deter herbivory may also have toxic effects on herbivores’ natural enemies (Ode, 2006). Therefore, to assess the costs, benefits, and ecological impacts of host plant resistance, it is critical to examine the effects of resistance on biological control agents. Specifically, it must be determined whether the resistance factors are biologically active against natural enemies and whether natural enemies encounter these factors while foraging for prey.
Most studies on the effects of host plant resistance on biological control agents have focused on fairly broad-spectrum defences that persist over time and are expressed throughout the plant, such as trichomes or insecticidal transgenes (Ode, 2006; Gatehouse et al., 2011). By contrast, fewer studies have examined the potential non-target impacts of monogenic resistance genes (R genes) in plants. These genes typically confer resistance against one or a small number of pest species, and may not be effective against all biotypes within the target species. Each R gene enables the host plant to recognize the presence of a specific gene product from avirulent biotypes of the pest which, in turn, triggers a rapid localized defence response at the site of attack (van Ooijen et al., 2007). Although the concept of R genes was first defined to describe plant–pathogen interactions (Flor, 1955), it has since been found to apply to many sources of resistance against insects, including the Hessian fly, aphids, and planthoppers (Smith and Clement, 2012). Because R-gene-mediated resistance relies on highly specific recognition events and on downstream defences that are induced rather than pre-formed, transient rather than persistent, and often local rather than systemic, non-target organisms are expected to have limited exposure to these defences. However, several recent studies indicate that R genes can nonetheless have non-target effects (Lundgren et al., 2009b ;Mitchell et al., 2010; Chacón et al., 2012; Ghising et al., 2012). Moreover, certain R genes have been demonstrated to respond to unrelated effectors from taxonomically divergent organisms (Lozano-Torres et al., 2012) and, to date, there are no accurate methods to predict the specificity of R genes based on nucleotide sequences or taxonomic relationships. Therefore, it is important to test the target range of R gene-mediated resistance empirically.
The Mi-1.2 herbivore resistance gene in tomato (Solanum lycopersicum L.) is a suitable system to study the specificity and potential non-target effects of R gene-mediated resistance because it affects a larger and more diverse set of pest species than any other known R gene. This gene, which is present in numerous commercial tomato cultivars, confers resistance against certain biotypes of the potato aphid Macrosiphum euphorbiae (Thomas) (Rossi et al., 1998), the sweetpotato whitefly Bemisia tabaci (Gennadius) (Nombela et al., 2001), the tomato psyllid Bactericerca cockerelli (Sulc) (Casteel et al., 2006), and certain species of root-knot nematode, Meloidogyne spp. (Milligan et al., 1998). All of these pests are piercing-sucking herbivores that feed on phloem sap and previous studies with aphids and nematodes indicate that resistance acts primarily by blocking the establishment of a feeding site in the vascular tissue of the plant (Dropkin, 1969; Kaloshian et al., 2000). These observations suggest that the effects of Mi-1.2 may be limited to phloem-feeding organisms; however, more recent studies of whitefly and aphid feeding behaviour on resistant plants indicate that Mi-mediated resistance also involves deterrent factors that herbivores encounter even before contacting the phloem (Jiang et al., 2001; Pallipparambil et al., 2010). These findings open the possibility that insect feeding guilds other than phloem sap-feeding herbivores could encounter Mi-mediated defences.
The potential non-target effects of the Mi-1.2 resistance gene in tomato on a zoophytophagous generalist predator, the minute pirate bug [Orius insidiosus (Say)] have been investigated here. Zoophytophagous predators have supplementary plant feeding behaviour, and are particularly important in providing consistent pest suppression because they are less likely to disperse or starve when herbivores are scarce (Eubanks and Styrsky, 2005). However, they may also be more vulnerable than strict predators to adverse effects of plant defences because of increased direct exposure. Orius insidiosus oviposit into leaf tissues and their preference for oviposition sites is influenced by surface characteristics of the host plant (Lundgren et al., 2008). Moreover, this species feeds on pollen, xylem sap, and the contents of epidermal and mesophyll cells in addition to preying on aphids and other small arthropods (Armer et al., 1998). Early instars of O. insidiosus rely heavily on plant feeding to meet their nutritional needs (Coll, 1996), and certain studies suggest that plant suitability for early instars may override prey availability for the predator. Therefore, O. insidiosus is a good species to use for initial risk assessments because it has high exposure levels to the host plant. Moreover, it is a common, commercially available biological control agent and a very influential species in food webs. Orius insidiosus feed on predaceous/herbivorous thrips, mites, aphids, and insect eggs and, in turn, fall prey to other predaceous arthropods including spiders, green lacewings, and other Hemipterans. Thus, this species can have a large impact on multitrophic population dynamics in agroecosystems.
To understand the potential effects of Mi-mediated resistance on this critical predator species, adult feeding behaviour, oviposition, nymphal emergence and survival on isogenic tomato lines with and without Mi-1.2, as well as their acceptance of prey items (aphids) reared on these genotypes were compared. Because it is critical to confirm that these predators interact directly with the plant tissues in which resistance is expressed, a combination of laser-capture microdissection and RT-PCR was also used to identify the tissue types in which Mi-1.2 is transcribed, and real-time PCR was performed to confirm the incidence of O. insidiosus feeding on plants with (Mi-1.2+) and without (Mi-1.2–) this resistance gene. Our broad objectives were to investigate the compatibility of a widely deployed R gene with a common biological control agent, and to shed light on the potential ecological impacts of R gene-mediated resistance.
Materials and methods
Plants and insects
This study used near-isogenic tomato cultivars with (cv. Motelle) and without (cv. Moneymaker) a ~650kb region carrying the Mi-1.2 resistance gene, and a transgenic line (143-25) that expresses Mi-1.2 driven by its native promoter in a Moneymaker background (Milligan et al., 1998). Tomato plants were used for experimentation at flowering, ~5 weeks after germination. Orius insidiosus were cultured in humidified plastic chambers (~24 °C, 16:8h light:dark) with Hydrocapsules® (Analytical Research Systems, Gainesville, FL) as a water source, Ephestia kuehniella Zeller eggs (Beneficial Insectary, Oak Run, CA) as a prey source, and green beans for oviposition and plant feeding. This study used a clonal population of the potato aphid (clone WU12) that can survive and reproduce on plants with Mi-1.2, although its population growth is greater on susceptible cultivars (Goggin et al., 2001, 2004; Cooper et al., 2004).
Orius insidiosus oviposition, emergence, and survival
Oviposition-deprived mated female O. insidiosus were enclosed in clip cages (5cm diameter) with moth eggs at uniform leaf positions on Moneymaker (Mi-1.2–), Motelle (Mi-1.2+), and 143-25 (Mi-1.2+) plants maintained in growth chambers (85% RH, 24 °C, 16:8h light:dark; 1 female per cage; 3 cages per plant; 10 plants per genotype). Adults were removed after oviposition (60h), and cages were observed daily to record the number of immatures that emerged. After all of the live insects reached the second instar, early-instar mortality was recorded and immatures were caged individually to prevent cannibalism (3–4 cages per plant, 1 immature per cage). Moth eggs were removed and cages were subsequently monitored daily until the insects molted to adulthood or died in order to calculate total mortality. The number of eggs laid by the original females during their 60h oviposition period was also determined at the end of the assay by detaching the leaves and observing them under a light microscope for hatched and unhatched eggs. Emergence was calculated for each cage by dividing the number of immatures observed by the number of eggs embedded in the leaf. The number of eggs laid, per cent emergence, per cent early-instar mortality, and per cent total mortality were analysed by ANOVA using JMP v9 (SAS Institute, Cary, NC, USA).
Orius insidiosus feeding behaviour
Choice and no-choice assays were used to determine whether Mi-1.2 influences O. insidiosus feeding behaviour on either plants or aphids. Adult females of O. insidiosus were deprived of plant materials for ~15h and were then caged individually in a transparent 0.2ml tube with either a resistant (Motelle, Mi-1.2+) or susceptible (Moneymaker, Mi-1.2–) leaf section (3mm2) for a no-choice bioassay (n=43), or with both the tissue types for a choice bioassay (n=50). Tubes were observed continuously for 1h, and feeding behaviours of the predator were recorded manually using the Etholog software version 2.25 (Ottoni, 2000). The feeding behaviour of O. insidiosus on aphid prey was determined using similar choice and no-choice assays, but instead of leaf materials, O. insidiosus adults were presented with first instar potato aphids that had been reared on either Mi-1.2+ or Mi-1.2– tomato plants. For predation assays, the predators were starved for ~18h prior to the no-choice (1h observation, n=9–11) and the choice bioassay (2h observation, n=17). The parameters recorded during the no-choice assays included the time at which the predator first touched the plant or probed the prey item with its stylets, the incidence and duration of this first contact and each subsequent contact, and the incidence and duration of grooming behaviour. The choice assays recorded which of the two plant or prey types was contacted first, as well as the number, incidence, and duration of contacts the predator made with each, and the incidence of aphid mortality. For the no-choice assays, the data were analysed by ANOVA. For the choice assays, all parameters were analysed using Chi-square (χ2) tests to determine if the proportion of times a specific plant genotype or plant-fed aphid was preferred by O. insidiosus (eg contacted first, contacted longer, etc) varied significantly from the 0.5 value that would be expected if host choice were based purely on random chance. When required, data were transformed using the best Box-Cox.
Molecular analysis to detect plant feeding
For 36h, O. insidiosus adult females were deprived of any plant substrate and were only provided moth eggs and hydrocapsules. Then the insects were caged individually on resistant (Motelle) or susceptible (Moneymaker) plants, or were maintained without a food source for the starved control group. After 16h of exposure, the insects were collected from the plants and flash-frozen for DNA extraction (19 individuals per plant genotype; 8 controls starved for 52h). To detect plant feeding in early instars, immatures were reared on resistant and susceptible tomato leaflets and were collected for analysis upon reaching the third instar (20 samples from resistant plants; 19 from susceptible plants; 6 starved control samples; 2 individuals/sample). DNA was extracted with the QIAamp DNA Mini Kit (Qiagen, Inc., Valencia, CA), and Q-PCR was performed on the DNA extracts using two primer sets: one targeting an actin gene from tomato (GQ339765.1), and another targeting a cytochrome oxidase 1 (Co-1) sequence from O. insidiosus (EF467230) (Table 1). Q-PCR was performed using an Mx3000P™ Real-Time PCR System (Stratagene; La Jolla, California) and the Clonetech SYBR®ADVANTAGE® qPCR premix Kit (Clonetech, Mountain View, CA) with the following PCR conditions: 10min at 95 °C, 40 amplification cycles (95 °C for 15 s, 55 °C for 30 s, 72 °C for 30 s, and data acquisition at the end of each cycle), and a final data acquisition step to generate melting curves from 65°C to 95°C every 0.3 °C. For each primer set, the amplification efficiency was calculated using the formula, E=10[–1/Ct slope] from data generated on serial dilutions of a set of bulked cDNA standards (Rasmussen, 2001). Relative quantification (RQ) values of PCR products were calculated using Pfaffl methodology (Pfaffl, 2001). Data from the tomato actin primers were normalized using the insect Co-1 primers to control for differences in insect sizes, and the PCR products from the actin primers in each experimental sample were quantified relative to the average cycle threshold (Ct) value of the starved control samples.
Table 1.
Primer sets
| Purpose | Target gene | Accession no. | Forward primer 5′–3′ | Reverse primer 5′–3′ | Size of amplicon from genomic DNA | Size of amplicon from cDNA |
|---|---|---|---|---|---|---|
| Molecular gut | ß-Actin | FJ532351.1 | GGAAAAGCTTGCC | CCTGCAGCTTCC | 180 bp | NA |
| content analysis | (tomato) | TATGTGG | ATACCAAT | |||
| Molecular gut | Co-I | EF467230 | ACACATTATTAGA | TAAATAGAAATA | 280 bp | NA |
| content analysis | (O. insidiosus) | AAAGAAAGAGGA | CGAATCCTAATG | |||
| In situ RT-PCR | Mi-1.2 | AF039682.1 | GCAAACAACTCAT | ACATCATCATCC | NA | 248 bp |
| (tomato) | TGGTGTT | AAAAGTGA | ||||
| In situ RT-PCR | Prosystemin | M84801 | AACAAAGGAGATG | CCTTTACATATC | NA | 200 bp |
| (tomato) | ACATGC | CTCCCTCC | ||||
| In situ RT-PCR | G2-LTF | TC118156 | CGCTTCGTTGATG | AGCTCTATCGCC | 500 bp | 186 bp |
| (tomato) | CTGTTAC | ATCCTTCA | ||||
| In situ RT-PCR | Rpl2 | NC_007898 | CATAGAAATCACA | GGGATGGTCTA | 265 bp | 265 bp |
| (tomato) | CTTGGAAAGG | CAGGGTTCA |
The RQ values of the samples were log2-transformed to stabilize variances and analysed by one-way ANOVA, and means for significant effects were separated using Student’s t-tests with JMP® v9.0 (SAS Institute, Cary, NC). To compare the proportion of each treatment group that was positive for plant DNA, samples were classified as positive for plant DNA if their RQ value was more than two standard deviations above the average RQ value for the starved controls. Then the percentages of positive samples were compared among treatment groups using Chi-square analysis.
Localization of Mi-1.2 transcripts
Tissue sections from petioles of Moneymaker (Mi-1.2–) and 143-25 (Mi-1.2+ Tr) were cryofixed as previously described (Nakazono et al., 2003), embedded in Tissue-Tek® OCT medium (Sakura Finetek USA, Torrance, CA), and cryosectioned at 20 μm and –19 °C using a Leica CM 3050S cryostat (Leica Microsystems, Frisco, Texas). Laser capture microdissection (PALM MicroLaser Systems, Zeiss, Bernried, Germany) was used to collect samples of phloem, epidermal, and mesophyll cells (5×106 μm2 area per sample; replicates from three plants per genotype for a total of 18 samples (see Supplementary Fig. S1 at JXB online). RNA was extracted from the catapulted tissue sections using the PicoPure™ RNA isolation kit (Arcturus, Sunnyvale, CA) and DNase treated using the RNase-free DNase set kit (Qiagen Inc, Valencia, CA). The Experion RNA HighSens Analysis Kit (Bio-Rad Laboratories, Wilmington, USA) was used to confirm RNA quality and integrity. A single round of amplification and cDNA synthesis were performed on ~1ng RNA per sample using the Arcturus® RiboAmp® HS PLUS 1.5 Round kit (Molecular Devices, Mountain View, CA) and Superscript III (Invitrogen, Carlsbad, CA). PCR was performed on ~80ng of cDNA/sample using primers to amplify Mi-1.2, Prosystemin, Ribosomal protein L2, and a G2-like transcription factor homologous to a phloem-specific (Banerjee et al., 2006) mRNA in potato (accession no. TC118156, Gene Index-DFCI) (Table 1). PCR conditions were as follows: 95 °C for 3min, 30 cycles (95 °C for 30 s, 55 °C for 30 s, 72 °C for 60 s), and 72 °C for 5min.
Results
Influence of resistance on O. insidiosus oviposition, emergence, and survival
To determine whether exposure to resistant plants has any direct effects on O. insidiosus, adults were allowed to oviposit on intact tomato plants, and rates of oviposition, emergence, and offspring survival were compared on three genotypes: a tomato cultivar that lacks Mi-1.2 (cv. Moneymaker, Mi-1.2–), a nearly-isogenic line that carries an ~650kb insertion containing Mi-1.2 (cv. Motelle, Mi-1.2+), and a line that expresses Mi-1.2 transgenically in a Moneymaker background (line 143-25, Mi-1.2+ Tr). Although rates of oviposition and offspring emergence were similar on all three genotypes (ANOVA: P >0.1), the percentage of offspring that died before reaching adulthood (total mortality; Fig. 1) varied significantly (ANOVA: P=0.0063). Total offspring mortality was ~2 times higher on the resistant cultivar Motelle (Mi-1.2+) than on the susceptible cultivar Moneymaker (Mi-1.2–) (Student’s t-test: P=0.0025), and ~1.8 times higher on 143-25 (Mi-1.2+ Tr) compared with Moneymaker (Student’s t-test: P=0.0151). Much of the observed mortality occurred in the first and second instars (early mortality; Fig. 1). Early instar mortality varied significantly among treatments (ANOVA: P <0.0001), and was ~9 times greater on Motelle (Student’s t-test: P <0.0001) and ~7 times greater on 143-25 (P=0.0001) than on the susceptible plants. Late instar mortality was not significantly different between resistant and susceptible plants (ANOVA: P >0.1). Offspring were provisioned with moth eggs from artificial diet-reared laboratory cultures to ensure that the quality of prey provided to the O. insidiosus was unaffected by the host plants; therefore, the high O. insidiosus mortality observed on genotypes that carry Mi-1.2 can be attributed to direct interactions between the plant and the predators. The fact that O. insidiosus survival on 143-25 was similar to survival on Motelle (Student’s t-tests: P >0.1) also indicates that the effects of plant genotype on predator survival were due to Mi-1.2 rather than to other linked genes in the 650kb introgressed region carried by Motelle.
Fig. 1.
Emergence and mortality of O. insidiosus immatures on intact plants with (+) and without (–) the Mi-1.2 resistance gene. Insect performance was measured in no-choice assays on the tomato cultivar Moneymaker (Mi-1.2–), the nearly isogenic cultivar Motelle (Mi-1.2+), and 143-25, a transgenic line that expresses Mi-1.2 in a Moneymaker background [Mi-1.2+ (Tr)]. The percentage of emergence (Mean±SEM) was calculated as (number of O. insidiosus emerged/number of eggs laid)×100. Early mortality denotes the percentage of emerged immatures that died in the first or second instar, and total mortality denotes the percentage of emerged immatures that died before reaching adulthood. Insect mortality on plant genotypes labelled with asterisks (*) are significantly different from that on the susceptible control line (Mi-1.2–) at α=0.05.
Influence of resistance on O. insidiosus feeding behaviour
Behavioural bioassays were conducted to determine if Mi-1.2 impacts feeding on plants or aphids by O. insidiosus. None of the feeding or grooming behavioural parameters that were measured differed significantly between treatments. When O. insidiosus were exposed to foliage from resistant and susceptible genotypes in no-choice bioassays, the predators made stylet contact with either plant tissue within ~5min of its introduction into the arena, indicating considerable interaction of the generalist predator with the first trophic level regardless of the plant genotype (Motelle, Mi-1.2+; Moneymaker, Mi-1.2–). The predator interacted equally with the resistant and susceptible plant genotypes in the no-choice (n=43, ANOVAs; P >0.1) and choice assays (n=50; χ2; P >0.1; Fig. 2). When O. insidiosus were exposed to aphids collected from resistant and susceptible genotypes in no-choice bioassays, the predators started to feed on the aphids within 10min after introduction into the arena and, in most cases, fed longer than 50% of the recording time, regardless of the source of aphids (Mi-1.2– or Mi-1.2+ plant fed). When given a choice between the two types of aphids, O. insidiosus prey feeding behaviour and aphid mortality did not suggest any significant preference between the two aphid types (χ2 tests: P >0.1; Fig. 3). The predator indiscriminately attacked aphids raised on either of the plant genotypes in both the no-choice (n=9, 11) and choice assay (n=17). In summary, our results indicated that O. insidiosus readily contacts tomato genotypes with and without Mi-1.2, in addition to accepting aphid prey reared on either genotype (Figs 2, 3).
Fig. 2.
Feeding behaviour of O. insidiosus on excised leaf tissue. (A) No-choice assay. Adults of O. insidiosus were caged individually with Mi-1.2– or Mi-1.2+ leaf sections (B) Choice assay. Each insect was enclosed with two leaf sections (Mi-1.2– and Mi-1.2+). Bars represent Mean±SEM. First SC (min)=the time elapsed before the insect first contacted the leaf tissue; first SC (#)=the percentage of insects in the choice assay that contacted the specified genotype before sampling the other genotype; total SC (#)=the total number of stylet contacts per insect; mean SC (min)=the mean duration per stylet contact per insect; and total SC (min)=the total duration of all stylet contacts per insect. (B) The percentage of O. insidiosus that had their first SC, their highest number of total SC, or their longest mean SC or total SC duration on Mi-1.2– (grey) versus Mi-1.2+ (black) tissues.
Fig. 3.
Feeding behaviour of O. insidiosus on aphids from Mi-1.2– or Mi-1.2+ tomato plants. (A) No-choice assay. One adult female of O. insidiosus was caged with one first instar aphid reared on either a Mi-1.2– or a Mi-1.2+ plant. (B) Choice assay. Each predator was placed in the choice arena with two aphids (1 from Mi-1.2– and 1 from Mi-1.2+ plants). Bars represent Mean±SEM. First SC (min)=the time elapsed before the predator began to stylet contact and probe the aphid; first SC (#)=the percentage of predators in the choice assay that contacted the specified aphid type before sampling the other aphid; total SC (#)=the total number of stylet contacts per predator; total SC (min)=the total duration of all stylet contacts per predator; CM (min)=time to confirmed aphid mortality; and CM(#)=proportion of predators that killed the specific aphid type before other. (B) The proportion of O. insidiosus individuals that had their first SC, their highest number of total SC, or their longest total SC duration on aphids from Mi-1.2– (grey) versus Mi-1.2+ (black) tissues.
Molecular analysis to detect plant feeding
Real-time PCR was used to detect tomato DNA in O. insidiosus adults and immatures exposed to resistant and susceptible plants in order to detect plant feeding and estimate its frequency on these two genotypes. Estimates of the abundance of tomato DNA in insect samples was normalized to estimates of insect DNA quantities to correct for possible variation in insect sizes. Relative quantification (RQ) values for tomato DNA were then calculated for each sample relative to the mean values for the negative controls (O. insidiosus that were deprived of plant materials for the duration of the experiment). For adults, there was a significant difference (ANOVA: P=0.0011) in the relative quantity of plant DNA present among the treatment groups (Mi-1.2+, Mi-1.2–, and starved), with significantly higher RQ values for insects that were exposed to resistant (Student’s t-test: P=0.0003) or susceptible plants (Student’s t-test: P=0.0031) compared with the starved controls (Fig. 4A). The average relative quantity of plant DNA in adults from susceptible plants was 1.6 times higher than the DNA content from resistant plants, but this difference was not statistically significant (Student’s t-test: P=0.229). For immature O. insidiosus, there was no significant difference in RQ values among the three treatment groups (ANOVA: P=0.3487), possibly because the relative quantities of plant DNA were highly variable (Fig. 4B). To explore variation that may have arisen from insects that did not feed, the proportion within each treatment group that was positive for plant DNA (i.e. those with RQ values more than two standard deviations above the average RQ value for the starved controls) was also examined. Compared with the starved controls which did not generate any samples above the RQ threshold, all other treatment groups had a significantly higher number of positive samples (Fig. 4C; Effect likelihood ratio tests: P <0.05), indicating that feeding occurred in all four treatment groups (adults and immatures exposed to Mi-1.2+ and Mi-1.2– plants). Feeding appeared to be more common among adults (68–72%) than immatures (22–32%).
Fig. 4.
Gut content analysis of O. insidiosus to detect plant feeding. Q-PCR was used to detect tomato DNA in O. insidiosus adults and immatures after the predators were allowed to feed on resistant (Motelle, Mi-1.2+) or susceptible (Moneymaker, Mi-1.2–) tomato plants. The starved control group was not fed any plant tissue for the duration of the experiment. The relative quantification (RQ) values for plant DNA in adults (A) and immatures (B) were normalized based on amplification of a DNA sequence from O. insidiosus, and were expressed relative to the mean cycle threshold (Ct) values for starved controls. (C) Insect samples were categorized as positive for plant DNA if their RQ values were greater than two standard deviations above the mean RQ value for the starved controls. Treatments labelled with asterisks (*) were significantly different from the corresponding starved control group at α=0.05.
Localization of Mi-1.2 transcripts
Orius insidiosus does not feed from the phloem like other pests that are impacted by Mi-1.2. To detect low levels of Mi-1.2 expression and to discriminate this gene from its many close homologues in tomato, a combination of laser capture microdissection (LCM) and RT-PCR were used to determine the localization of Mi-1.2 transcripts in resistant plant tissues. Cryosectioning and LCM were used to dissect samples of epidermal, mesophyll, and phloem tissues from tomato plants that lack Mi-1.2 (cv. Moneymaker), and isogenic transgenic plants (143-25) that express Mi-1.2 driven by its native promoter in the same genetic background (cv. Moneymaker). RT-PCR performed on RNA from the harvested tissue provided evidence that the Mi-1.2 gene is transcribed in all three tissue types (Fig. 5A). The experiment was repeated three times using separate plants. In 143-25, Mi-1.2 transcripts were detected in all three samples of epidermis tissue, two out of three samples of mesophyll tissue, and one out of three samples of phloem tissue. Primers to detect Mi-1.2 expression did not generate PCR products from any of the tissue samples from susceptible plants, indicating that our primers did not amplify any of the Mi-1 homologues present in this genetic background. The presence of cDNA in all samples was confirmed by amplifying transcripts encoding the ribosomal protein RPL2 (Fig. 5A). Primers for prosystemin and a G2-like transcription factor (G2-LTF), which are expressed specifically in the phloem, detected transcripts in the phloem samples but not in any of the epidermis or mesophyll samples, providing evidence that the LCM sectioning adequately isolated the tissue types (Fig. 5A). The prosystemin primers generated PCR products in two out of the three phloem samples, while G2-LTF expression was detected in all three phloem samples. Results for the G2-LTF primers also indicated that our samples were free of contamination from genomic DNA. This primer set flanks an intron and generates a PCR product of ~500bp from genomic DNA samples, whereas it only yields a single amplicon of 186bp from our cDNA samples (Fig. 5B).
Fig. 5.
Localization of Mi-1.2 transcripts in tomato tissues. (A) RT-PCR was used to assess expression of Mi-1.2 in epidermis (E), mesophyll (M), and phloem (P) samples harvested by LCM from the petioles of 143-25 (Mi-1.2+) and the susceptible cultivar Moneymaker (Mi-1.2–). Primers to the ubiquitously-expressed housekeeping gene Ribosomal protein L2 (Rpl2) were used to confirm good cDNA synthesis, and primers that amplify phloem-specific transcripts (Prosystemin and G2-like transcription factor) were used to confirm that the microdissection procedure adequately separated vascular and non-vascular tissues. (B) The G2-like transcription factor (G2-LTF) primers were also used to confirm the absence of genomic DNA in the samples, because the primers flank an intron and generate different amplicon sizes from genomic DNA (G) versus our cDNA templates. The gel lanes in this figure were spliced and rearranged to conveniently compare gene expression among the targeted tissues.
Discussion
The objective of our study was to evaluate the influence of R-gene-mediated resistance in tomato on a common insect predator that feeds supplementally from host plants. Our results showed for the first time that Mi-mediated resistance in tomato could have direct non-target effects on a biological control agent. Early instars of the zoophytophagous predator O. insidiosus had significantly reduced survival on plants with Mi-1.2 compared with isogenic susceptible controls (Mi-1.2–), even when the predators were provisioned with moth eggs whose quality was unaffected by the host plant. In behavioural assays, resistance did not impact rates of plant sampling by adult predators (Fig. 2); moreover, molecular gut content analysis confirmed that adult and immature O. insidiosus fed on both resistant and susceptible plant genotypes. These data suggest that the deleterious effects of resistant plants on O. insidiosus were due to antibiosis rather than antixenosis. However, in our molecular gut content analysis, there was a trend for lower levels of plant contents in insects exposed to resistant plants compared with insects on susceptible genotypes. Therefore, non-preference may also contribute to the effects of Mi-mediated resistance on O. insidiosus. Further, it is possible that our behavioural studies with adult O. insidiousus may not reflect the behaviour of all developmental stages; although early-instar nymphs are the life stage most impacted by Mi-1.2, behavioural assays with this life stage were not performed because they are very delicate and are prone to injury when handled.
Orius insidiosus is known to feed on xylem sap, pollen, and cell contents from epidermal or mesophyll layers, but monitoring of radiolabelled tracers indicates that it does not ingest phloem sap (Armer et al., 1998). Thus, O. insidiosus is the first organism to be impacted by Mi-1.2 that falls outside the feeding guild of herbivores that specialize on phloem sap. Consistent with this observation, it has been confirmed that the Mi-1.2 gene is expressed in the epidermis and mesophyll in addition to the vasculature. Furthermore, recent electrophysiological observations of aphid and whitefly feeding behaviour on plants with Mi-1.2 suggest that these insects are also impacted by deterrents located outside the phloem. The slender, tubular mouthparts of aphids and whiteflies penetrate between the cells of the epidermis and mesophyll, but will intermittently sample these cells en route to the phloem. Electrical penetration graph recordings of aphids and whiteflies on plants with and without Mi-1.2 indicate that this sampling behaviour is delayed on resistant varieties, suggesting that these insects may encounter deterrents that act in the intercellular spaces of the epidermis or mesophyll (Jiang et al., 2001; Pallipparambil et al., 2010). Together, these observations suggest that Mi-mediated resistance involves recognition events and defence responses that occur in the epidermis or mesophyll, rather than depending solely upon phloem-limited defences. Moreover, our observations indicate that Mi-1.2 can impact a greater ecological diversity of organisms than previously assumed.
The vast majority of previous studies on the non-target impacts of herbivore resistance in plants have focused on transgenic traits such as the expression of Cry toxins from Bacillus thuringiensis Berliner, because there are regulatory requirements for assessing the risks of genetically modified crops (Lundgren et al., 2009a ; Gatehouse et al., 2011). Fewer studies have examined the potential non-target effects of resistant crop varieties developed through traditional breeding and, of these, only a handful have explored the impacts of R genes, which have typically been assumed to have very narrow target ranges. In rice, alfalfa, and wheat, R genes conferring aphid or planthopper resistance have been reported to be compatible with biological control, with no negative effects detected on predators or parasitoids (Salim and Heinrichs, 1986; Farid et al., 1997, 1998a , b ; Messina and Sorenson, 2001; Bosque-Pérez et al., 2002; Giles et al., 2002). However, in raspberry, lower parasitoid attack rates were observed on plants carrying the A10 aphid resistance gene than on susceptible checks, possibly due to lower aphid densities and the increased incidence of aphids dropping off the resistant plants (Mitchell et al., 2010). Moreover, in soybean, the Rag1 aphid resistance gene appears to have direct negative effects on the zoophytophagous predator Harmonia axyridis (Pallas), and also reduces attack rates and adult emergence of Binodoxys communis (Gahan), a parasitoid of aphids (Lundgren et al., 2009b ; Chacón et al., 2012; Ghising et al., 2012). These results demonstrate that non-target effects are not limited to genetically modified crops, and that even R gene-mediated resistance can directly impact the third trophic level.
Our findings also indicate that there is a need to characterize plant responses to O. insidiosus and other zoophytophagous predators. The fact that the Mi-1.2 R gene impacts O. insidiosus suggests that effectors from this insect elicit a defence response in the host plant. Because omnivorous Heteropterans such as O. insidiosus utilize extra-oral digestion, they inject enzyme-rich saliva into their hosts and these secretions could trigger plant defences or enhance the suitability of susceptible hosts similar to oral secretions from caterpillars, grasshoppers, aphids, and other herbivores. Moreover, research with other herbivores has revealed that plant defence responses can be triggered by a variety of other cues from insects, including oviposition damage, egg deposition, and even walking (Peiffer et al., 2009). Therefore, the presence of omnivores and other natural enemies on plants could modify the suitability of host plants for both zoophytophagous species and herbivores. For example, salivary extracts from the omnivorous species Lygus hesperus Knight alter plant volatile emissions (Rodriguez-Saona et al., 2002), feeding by Tupiocoris notatus (Distant) modifies photosynthetic rates (Halitschke et al., 2011), and oviposition by O. laevigatus (Fieber) induces wound-responsive defences that decrease infestations by the Western flower thrips Frankliniella occidentalis (Pergande) (De Puysseleyr et al., 2011). Mostly though, little is known about the salivary excretions of O. insidiosus and other zoophytophagous species, or about their impact on induced defences in host plants. Further research is required to understand and predict their tritrophic interactions with plants and herbivores.
Field studies are also needed to assess the overall impact of Mi-1.2 on biological control agents in tomato. While controlled studies in the laboratory, growth chamber, or greenhouse have the greatest power to detect negative impacts of host plant resistance on natural enemies and to decipher the mode of action of these effects, field experiments have greater power to evaluate the real-world consequences of these effects for pest management (Romeis et al., 2011). The net effect of Mi-mediated resistance on O. insidiosus predation rates under field conditions will depend in part upon (i) the effects of resistance on prey abundance, densities, spatial distributions, size and quality; (ii) the potential for O. insidiosus to compensate for low-quality host plants by increasing their rate of prey consumption; and (iii) their ability to escape resistance in time or space by feeding on tissues in which Mi-mediated aphid resistance is not active, such as floral apexes (Kaloshian et al., 1995). Furthermore, the net effect of Mi-1.2 on pest populations under field conditions will depend upon the relative weight of bottom-up versus top-down effects on herbivores. For example, resistant soybean cultivars provided improved management of the Mexican bean beetle Epilachna varivestis Mulsant despite the fact that they reduced attack rates by the predator Podisus maculiventris (Say) (Bartlett, 2008). Similarly, although resistant varieties of Vicia faba L. appeared to increase the development time and reduce the fecundity of the predator Coccinella septempunctata L., aphid numbers were lowest when the two management strategies were combined (Shannag and Obeidat, 2008). In fact, many studies report that biological control is most likely to achieve economically acceptable results when deployed in combination with a crop variety that is at least partially resistant to the target pest (Van Emden, 1995). Indeed, supplemental control strategies such as biological control are particularly important for crops in which only partial resistance is available. In the case of tomato cultivars that carry the Mi-1.2 gene, biotypes of the potato aphid have been identified that are partially or fully tolerant to resistance (Rossi et al., 1998; Hebert et al., 2007), and so supplemental control strategies are needed to manage these virulent or semi-virulent populations. Moreover, O. insidiosus preys on mites, thrips, and other pests that are not managed by Mi-mediated resistance. In short, any cost–benefit analysis of host plant resistance must take into consideration the full suite of pests and beneficial insects that are present, and measure the independent and combined effects of resistance and biological control agents on pest populations.
Supplementary data
Supplementary data can be found at JXB online.
Supplementary Fig. S1. Micrographs obtained from PALM RoboSoftware show dissection of (A) phloem tissue, and (B) mesophyll and epidermis from cryosections of tomato leaf petioles using the Laser Capture Microdissection (LCM) technique.
Acknowledgements
We thank Clinton Trammel, Lingling Jia, Jun Shen, Carlos Avila, Jingjing Xie, Fengying Shi, Bob Dienglewicz, David McNabb, Andronikos Mauromoustakos, John Guerber, Allen Szalanski, Ashley Dowling, Ken Korth, Wayne Kuenzel, Ines Pinto, Hong Li Wang, and Gisela Erf for advice and assistance with experiments, equipment, and statistics. This research was supported by the National Research Initiative of the USDA Cooperative State Research, Education and Extension Service Grant 2006-35607-330 16612 awarded to FLG.
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