Ecological Applications, 20(1), 2010, pp. 242–250 Ó 2010 by the Ecological Society of America Host-adapted parasitoids in biological control: Does source matter? LEE M. HENRY,1,5 NIGEL MAY,1,2 SUSANNA ACHEAMPONG,3,4 DAVID R. GILLESPIE,1,3 AND BERNARD D. ROITBERG1 1 Department of Biological Sciences, Simon Fraser University, Burnaby, British Columbia V5A 1S6 Canada School of Computing, British Columbia Institute of Technology, Burnaby, British Columbia V5G 3H2 Canada 3 Pacific Agri-Food Research Centre, Agriculture and Agri-Food Canada, POB 1000, Agassiz, British Columbia V0M 1A0 Canada 4 British Columbia Ministry of Agriculture and Lands, 200–1690 Powick Road, Kelowna, British Columbia V1X 7G5 Canada 2 Abstract. It has been hypothesized that the success of a biological control introduction is, in part, dependent on the ability of the control agent to become established in its new environment or to its new population of hosts through local adaptation. Despite this, few studies have investigated the influence of the recent coevolutionary history of pest species and natural enemies on the efficacy of biological control agents, especially for agents that are massreared for release in agriculture. We investigate the evolutionary potential of a biological control agent Aphidius ervi to adapt to a key pest species, the foxglove aphid Aulacorthum solani, through components essential to the evolution of parasitoid virulence. We explored (1) the influence of genetic variation from natural source populations on the ability to parasitize natal and non-natal host species; (2) the heritability of key traits related to parasitoid fitness; and (3) the efficacy of parasitoid host-selection lines in a greenhouse system. Source populations maintained genetic variation in the ability to utilize natal and non-natal host species; however, only some of the traits sampled suggested local adaptation of parasitoid populations. The ability to parasitize a host was found to be genetically determined and strongly heritable, irrespective of host species. The greenhouse study demonstrated the potential of parasitoid selection lines to substantially increase performance of parasitoids for target pest species. This research provides insight into novel techniques that can be used to increase the quality of biological control agents through the development of lines of natural enemies adapted to particular pest species. Key words: Acyrthosiphon pisum; adaptive evolution; Aphidius ervi; Aulacorthum solani; biological control; foxglove aphid; heritability; parasitoid; pea aphid; reciprocal transplant; selection experiment. INTRODUCTION Research in population ecology has been an essential component in the practical application of natural enemies in controlling pests, but the importance of genetics and adaptive evolution in biological control remains a controversial topic (Force 1967, Remington 1968, Messenger and van den Bosch 1971, Roush 1990, Hopper et al. 1993, Holt and Hochberg 1997, Jervis 1997, Hufbauer 2002, Hufbauer and Roderick 2005, Phillips et al. 2008). Recent research has sought to better understand the genetic structure of natural enemy populations in an attempt to identify populations that are locally adapted to environmental conditions or the organisms with which they interact (Lozier et al. 2008, Philips et al. 2008). However, few studies attempting to increase the efficacy of biological control agents have considered the recent coevolutionary history between pest species and natural enemies. Furthermore, the role of adaptive evolution in biological control has been addressed primarily from classic introductions of natural enemies to control exotic pests, with the Manuscript received 10 October 2008; revised 16 March 2009; accepted 21 April 2009. Corresponding Editor: M. P. Ayres. 5 E-mail: [email protected] 242 adaptive potential of natural enemies used in greenhouses and other areas of agriculture being virtually ignored. The value of natural enemies as an integrative method of controlling pests in greenhouses is well recognized (van Lenteren 2000). A zero-tolerance policy for pest damage in commercial vegetable and flower markets and an increasing desire to reduce pesticide applications has made the continual improvement of biological control efforts a top priority of the greenhouse industry in general (van Lenteren 1997). Difficulty establishing natural enemy populations, unpredictable control of problematic pests by natural enemies, and lag periods associated with natural enemy adjustment to novel host species are some of the major current issues in biological control. Recently a movement to improve biological control efforts has emerged in the form of breeding pest and disease resistance in plants (Cuartero et al. 1999) or breeding plants that facilitate natural enemy foraging. Examples include selected cucumber lines with fewer hairs to increase searching efficiency of parasitoids (van Lenteren et al. 1995) and the cultivation of plant lines that produce greater amounts of natural enemy-attractive volatiles to decrease the response time to infestation (Dicke 1999). This artificial selection approach has demonstrated the potential of breeding programs in pest January 2010 HOST-ADAPTED PARASITOIDS IN BIOCONTROL control; however, surprisingly little to no effort has been made to actually breed the natural enemies themselves in an attempt to improve efficacy of biological control agents. (For an exception see Croft et al. 1999.) Insect parasitoids are one of the most common natural enemies used in greenhouse pest management. Generalist parasitoids used as biological control agents are often assumed to be equally capable of effectively utilizing all recorded host species. However, generalist parasitoids, like most generalist insects that are largely polyphagous at the species level, often exhibit limited host species use at the population or community level (Fox and Morrow 1981, Smith et al. 2007). Variation in the ability to parasitize natal and non-natal host species has been recorded for several aphid parasitoids, suggesting a genetic basis for virulence and resistance across a variety of systems (Powell and Wright 1988, Pennacchio et al. 1994, Henter 1995, Pike et al. 1999, Antolin et al. 2006). Recent research by Henry et al. (2008) demonstrated the potential of Aphidius ervi to adapt to a key greenhouse pest species, the foxglove aphid Aulacorthum solani, under controlled laboratory conditions. Evidence of host adaptation in generalist parasitoids has also been revealed in several biological control introductions in natural systems, in that parasitoids were shown to have dramatically increased their reproductive potential on a novel host species following the initial introductions (van den Bosch 1964, Lemasurier and Waage 1993). These examples provide strong evidence for the capability of generalist parasitoids to adapt to key pest species. However, to the author’s knowledge, no studies have initiated the first steps toward breeding programs for pest-adapted biological control agents or directly tested the efficacy of host-adapted parasitoids in a commercial greenhouse setting. Theoretically, several possible evolutionary interactions may occur between parasitoids and their hosts, including evolved host resistance to parasitoid attack and the evolution of parasitoid virulence to overcome host defenses. The interplay of these coevolving factors is fundamental to the patterns of parasitism found in communities of parasitoids and their hosts. The primary objective of this study is to focus on the evolutionary potential of parasitoids in their ability to parasitize different host species to determine if parasitoid efficacy can be increased. The potential for hosts to evolve resistance to parasitism is not explicitly measured within this study; however, it is recognized as an essential component of host–parasitoid coevolution in natural and agricultural systems. The parasitoid A. ervi represents an exemplary system to address the adaptive evolution of natural enemies used in biological control because it is not only a commonly used parasitoid to control aphids in agriculture, but also a model system in ecology and evolutionary biology (e.g., Sequeira and Mackauer 1992, Henter 1995). The potential of A. ervi to adapt locally to two 243 aphids, Acyrthosiphon pisum and A. solani, was investigated. These aphids represent important examples of hosts with which A. ervi is associated in agriculture, as A. pisum is the most common host used to commercially mass rear colonies of A. ervi, and A. solani is an extremely problematic aphid pest worldwide that is historically difficult to control with biological control introductions (Sanchez et al. 2007). In the past, Aphidius parasitoids have been used as the primary biological agent to control A. solani, although the results are often unpredictable. We used a series of experiments to investigate the potential of A. ervi to adapt to different host species. First, we determined if natural populations of parasitoids are locally adapted to the host species most prevalent in their environment. This addresses the importance of source populations in collecting parasitoids for use in mass-rearing programs. Second, we investigated the heritability of three traits fundamental to parasitoid performance as biological control agents. Establishing trait heritability is an important first step in the implementation of artificial selection and breeding programs of pest-adapted biological control agents. Third, using a ‘‘quasi-natural’’ selection experiment, we established the potential of parasitoids that have been preadapted to a pest species to outperform parasitoids that have been reared on a standard rearing host in a simulated commercial greenhouse setting. MATERIALS AND METHODS Parasitoid and aphid collections and rearing Parasitoids and aphids used in the reciprocal transplant and heritability experiments were collected from foxglove aphids Aulacorthum solani (Kaltenbach) (Hemiptera: Aphididae), feeding in large organic potato (Solanum tuberosum L.) fields (;10 km2 field) in Delta, British Columbia, Canada, and pea aphids Acyrthosiphon pisum (Hemiptera: Aphididae), feeding in alfalfa (Medicago sativa L.) fields (;3 km2 field) in Agassiz, British Columbia, Canada. Several hundred parasitoids were collected by the removal of mummies from leaf material as well as by rearing aphids that harbored parasitoids. (A mummy is an aphid exoskeleton containing a parasitoid pupa. This occurs after the larval parasitoid has consumed the host aphid and is metamorphosing into an adult.) All aphids were collected using sweep nets. Upon emergence, female parasitoids were individually given access to ;30 mixed instars of their natal hosts; then the females were identified, and the offspring of each identified female were used to propagate species-specific colonies of Aphidius ervi Haliday (Hymenoptera: Aphidiidae). Parasitoids and aphids were identified by taxonomic keys and by comparison to identified, exemplar specimens at the Pacific Agri-Food Research Centre in Agassiz (Agriculture Canada). Pea aphids were the only aphid species collected from the alfalfa field, but the potato fields harbored a community of aphid species 244 LEE M. HENRY ET AL. dominated by foxglove, potato (Macrosiphum euphorbiae) (Thomas), and green peach aphids (Myzus persicae) (Sulver), and potentially other species at lower frequencies. However, A. ervi from the potato fields that were used in this study were all confirmed to be from foxglove aphids by identifying and isolating the aphids (many of which were already parasitized), then collecting mummies from the isolated foxglove aphid population. Aphids were maintained on cuttings of their host species of origin, with the petiole inserted into water in clear plastic cups covered with tissue paper. A. ervi were maintained using the same system, with the addition of dilute honey for sustenance. Twenty replicate cups were maintained for each aphid host species, with 10 cups per host species maintaining the parasitoid populations. Reciprocal transplant experiment A. ervi collected from A. solani on potato and A. pisum on alfalfa were experimentally assayed on the host species from which they were originally collected (natal host), and the novel (non-natal) host species using a reciprocal transplant design. Natal and non-natal will be used as terms to describe the host species from which the parasitoids were collected; however this does not reflect the history of host use, as individuals from both populations may have previously utilized alternate host species. Individual females (N ¼ 40) were given access to a patch of 20 second-instar pea or foxglove aphids feeding on a leaf cutting. Each female was allowed to forage on a single aphid patch for two hours, at which time the parasitoid was removed, and the aphids were left on the leaf to develop. Each parasitoid was used only once and then preserved in 75% ethanol after each trial to confirm the parasitoid species if necessary. Total parasitism (number of mummies formed per 20 aphids), the proportion of offspring emerging from the mummies, and the sex ratio of the offspring (proportion female) served as proxies for parasitoid fitness. Natal host species of the parasitoid, the host species the parasitoid was assayed on (exposure host), and the interaction between natal and exposure host species were compared for each of the proxies. The number of mummies formed was analyzed by ANOVA. The proportion of emergence and sex ratio were not normally distributed and were therefore analyzed using a generalized linear model (GLM) with a binomial distribution and a logit function. Heritability experiment A mother 3 daughter regression was used to determine the narrow-sense heritability (h2) of three traits integral to parasitoid fitness: total parasitism, proportion of offspring emergence from mummies, and offspring sex ratio. Only A. ervi from the population collected on pea aphids, feeding on alfalfa, were used for this experiment; however, heritability estimates were determined for performance on both pea and foxglove Ecological Applications Vol. 20, No. 1 aphids. Female parasitoids (mothers) were assayed on their natal host species (N ¼ 42) using the same protocol as in the previous experiment (i.e., 20 second-instar aphids in a petri dish for two hours). Upon emergence, each mother’s offspring were allowed to inbreed to reduce genetic variability, and then four female offspring were randomly selected and assayed on pea and foxglove aphids (two daughters assayed on pea and two daughters assayed on foxglove). Zero trait values of daughters were removed from the analyses, as we could not determine if a value of zero was due to genetic components or other biological reasons (e.g., zero sex ratio could be due to not mating, or zero parasitism may be due to an unresponsive female). Heritability was determined using mothers and daughters assayed on the same host species (i.e., genetic component only, controlling for environment). A comparison of inbred sisters from the same family assayed on the two different host species was used to determine if the expression of a phenotype is influenced by the species of the host (i.e., environmental effects). This design allowed us to determine trait heritability using a mother 3 daughter regression while controlling for potential environmental effects caused by developing in different host species. Narrow-sense heritability of the aforementioned traits was estimated using a one-parent 3 mid-offspring (mean trait value of daughters) regression, with the coefficient of the slope of the linear regression line approximating heritability (Falconer and Mackay 1989). As only female phenotypes could be measured, the estimate of heritability (h2) is double the coefficient of the slope (singleparent heritability). Each trait was analyzed using a linear regression comparing mothers and daughters reared on pea aphids and foxglove aphids separately, blocking for mother (six linear regressions in total). The relationship between sisters reared on separate host species was assessed using a linear regression, blocking for mother, by plotting the trait value of pea aphidreared sisters against the trait of foxglove aphid-reared sisters for each fitness proxy. The relationship between sister traits was analyzed separately for families that had emerged from pea and foxglove aphids, in order to control for potential maternal effects caused by developing in different host species. Host-adapted parasitoid greenhouse experiment Parasitoids used in the greenhouse experiment were from selection lines that had been isolated and maintained in replication on either pea or foxglove aphids at Simon Fraser University for two years (;50 parasitoid generations), as described in Henry et al. (2008). A. ervi selection lines were assayed for their performance on foxglove aphids in a controlled greenhouse experiment at the Pacific Agri-Food Research Centre in Agassiz. Mature pepper plants (;two months old), isolated in screened individual enclosures, in a 6.4 3 15 m greenhouse, were each heavily infested with several thousand foxglove aphids and left for a week for January 2010 HOST-ADAPTED PARASITOIDS IN BIOCONTROL 245 the aphids to become established. Plants were infested to the point where parasitoids would not be limited by host abundance. Parasitoid mummies were randomly chosen from the replicate populations of host-selection-line parasitoids. Parasitoids were isolated by host species and allowed to mate; then 10 females were released in each enclosure by leaning an unsealed test tube containing the parasitoids against the basal stem of the pepper plant (N ¼ 10 replicates for each selection line). The parasitoids were left to forage on the infested plants within the enclosures for a 12-d period. This time frame was long enough that the parasitoids from the initial release had died, and no new parasitoids had emerged to additionally parasitize the aphids. Plants were supplied with water using a drip irrigation system but were otherwise not tended for the course of the experiment. After the plants were removed from the enclosures and dissected, all mummies were removed and counted. The dissected plants were then individually placed in Plexiglas containers with fresh pepper plants to allow the aphids still harboring parasitoid larvae access to fresh plant material, where larvae developed into mummies. This methodology resulted in a precise value for total parasitism per plant (total mummies). Total parasitism was compared by parasitoid selection line (ANOVA). All statistical analyses were performed using JMP 7.0 statistical software (SAS Institute 2007). RESULTS Reciprocal transplant The total number of mummies formed differed when comparing parasitoids from the two host species populations (F3, 154 ¼ 39.3, P , 0.0001). Parasitoids collected from the pea aphid population produced more mummies (12.6 6 0.45) in general than parasitoids from the foxglove population (10.4 6 0.49) (natal host: F1, 154 ¼ 10.2, P ¼ 0.0017), and parasitoids generally produced more mummies when exposed to foxglove aphids (14.6 6 0.46) compared to pea aphids (8.5 6 0.48) (exposure host: F1, 154 ¼ 87.9, P , 0.0001). All values are mean 6 SE. Parasitoids produced significantly more mummies on their natal host (natal 3 exposure: F1, 154 ¼ 25.4, P , 0.0001), as indicated by the strong interaction between natal and exposure host species, which suggests parasitoids are locally adapted to their natal host species (Fig. 1A). The proportion of emergence from mummies (GLM: v23; 140 ¼ 93.65, P , 0.0001) differed between the two parasitoid populations. The proportion of emergence was greater from foxglove aphids at 0.90 6 0.03 compared to pea aphids at 0.81 6 0.03 (exposure host: v21; 140 ¼ 22.90, P , 0.0001). Parasitoids from the pea aphid population generally had higher emergence on both host species (0.91 6 0.03) compared to parasitoids from the foxglove population (0.80 6 0.03) (natal host: v21; 140 ¼ 68.62, P , 0.0001; Fig. 1B). Parasitoids from the foxglove population had a substantially lower proportion of offspring emerging from pea aphids (0.69 6 0.04) FIG. 1. Hymenopteran parasitoids (Aphidius ervi) collected from pea aphid (Acyrthosiphon pisum) and foxglove aphid (Aulacorthum solani ) populations assayed on natal and nonnatal host species. Parasitoid performance is indicated by (A) the parasitism of 20 aphids; (B) the proportion of offspring emerging from parasitized aphids (i.e., emergence success); and (C) the sex ratio of the emerging offspring (proportion of females). Values are means 6 SE. compared to emergence from their natal host species (0.88 6 0.04) (natal 3 exposure: v21; 140 ¼ 9.15, P ¼ 0.0025). No variation was detected in the sex ratio of emerging offspring (v23; 108 ¼ 2.71, P ¼ 0.44; Fig. 1C). 246 Ecological Applications Vol. 20, No. 1 LEE M. HENRY ET AL. from mummies for parasitoids assayed on pea aphids did not display heritable variation (h2 ¼ 0.18 6 0.26) (F1,46 ¼ 0.49, P ¼ 0.49). The sex ratio of offspring from pea aphid-assayed parasitoids did not show heritable variation (h2 ¼ 1.72 6 0.85) (F1,20 ¼ 4.11, P ¼ 0.07; Table 1). The comparison of the parasitism of sisters assayed on pea and foxglove aphids had a significant negative relationship when the families had emerged from pea aphids (F1,47 ¼ 8.79, r 2 ¼ 0.16, P ¼ 0.0048; Fig. 3B). However, no relationship was detected in the parasitism of sisters assayed on the two host species when families had emerged from foxglove aphids (F1,57 ¼ 0.99, r 2 ¼ 0.02, P ¼ 0.32; Fig. 3A). The proportion of offspring emergence of sisters assayed on different hosts did not show a relationship when the families had emerged from foxglove (F1,52 ¼ 0.89, r 2 ¼ 0.02, P ¼ 0.35) or pea aphids (F1,39 ¼ 0.79, r 2 ¼ 0.02, P ¼ 0.38). No relationship was detected in the sex ratio of the offspring from families reared on foxglove (F1,20 ¼ 0.22, r 2 ¼ 0.01, P ¼ 0.64) or pea aphids (F1,15 ¼ 0.001, r 2 ¼ 9.7 3 105, P ¼ 0.97). Host-adapted parasitoid greenhouse experiment Parasitoids from the foxglove and pea aphid selection lines differed in their ability to parasitize foxglove aphids in a greenhouse setting (F1,16 ¼ 5.58, P ¼ 0.03). Parasitoids from the foxglove aphid selection line produced an average of 233.8 6 51.7 mummies, whereas parasitoids from the pea aphid selection line produced an average of 86.5 6 31.4 mummies. DISCUSSION FIG. 2. Heritability of parasitism using a one-parent (mother) 3 offspring (daughter) regression for parasitoids reared on (A) foxglove aphids and (B) pea aphids. Each point represents one family, with the mother’s parasitism on the xaxis and the mean value of two of her daughters (mid-daughter) on the y-axis. Axis scales (the number of mummies formed out of 20 aphids [i.e., parasitism]) represent the deviation from the mean value (0) of all parents (x-axis) and all offspring (y-axis). Estimates of heritability Significant heritable variation in the ability to parasitize foxglove aphids was demonstrated by the mother 3 daughter regression (h2 ¼ 0.95 6 0.16) (linear regression: F1,59 ¼ 35.2, P , 0.0001; Fig. 2A). The proportion of offspring emergence from mummies did not display heritable variation for foxglove-assayed parasitoids (h2 ¼ 0.30 6 0.46) (F1,58 ¼ 0.41, P ¼ 0.52). Additionally, offspring sex ratio did not display heritable variation when parasitoids were assayed on foxglove aphids (h2 ¼ 0.64 6 0.56) (F1,42 ¼ 1.31, P ¼ 0.27; Table 1). A similar pattern emerged when parasitoids were assayed on pea aphids. Significant heritable variation was detected in the parasitism of mothers and daughters exposed to pea aphids (0.75 6 0.28) (F1,47 ¼ 7.06, P ¼ 0.011; Fig. 2B). The proportion of offspring emergence It has been suggested that the success of biological control is primarily based on the quality of the natural enemies produced by commercial suppliers (van Lenteren 1997). Developments in the mass production, quality control, storage, and shipment of natural enemies have decreased production costs and led to better product quality (van Lenteren 2000). However, the importance of genetic variation of natural enemies, biotypes for mass rearing, and recent coevolutionary history of parasitoids with host species has not been addressed for biological control agents used in agriculture. This is surprising, given that the closed nature of greenhouses in particular make them ideal for releasing preadapted biological control agents, and commercial biocontrol-rearing facilities are an ideal arrangement for the establishment of natural enemy breeding programs. Patterns of parasitism and evidence of local host adaptation The reciprocal transplant experiment provides evidence that wild host-associated parasitoid populations maintain genetic differences that influence their ability to utilize natal and non-natal host species. However, only some of the traits sampled indicate patterns of local adaptation. The patterns of parasitism from the reciprocal transplant experiment suggest that parasitoids are locally adapted to their natal host populations, given January 2010 HOST-ADAPTED PARASITOIDS IN BIOCONTROL 247 TABLE 1. Heritability estimates (h2) of a one-parent 3 mid-offspring regression, using mothers and daughters of the hymentopteran parasitoid Aphidius ervi reared on either pea or foxglove aphids. F P r2 h2, mean 6 SE 35.2 0.41 1.31 ,0.0001 0.52 0.27 0.38 0.01 0.06 0.95 6 0.16 0.30 6 0.46 0.64 6 0.56 7.06 0.49 4.11 0.011 0.49 0.07 0.13 0.02 0.31 0.75 6 0.28 0.18 6 0.26 1.72 6 0.85 Species/phenotypic trait Pea aphid (Acyrthosiphon pisum) Parasitism Proportion of offspring emerging Sex ratio Foxglove aphid (Aulacorthum solani ) Parasitism Proportion of offspring emerging Sex ratio Note: Mothers and daughters were always assayed on the same host species. that parasitoids from both populations maintained a higher level of parasitism on their natal host (Fig. 1A). Parasitoids from the pea aphid population maintained a relatively high level of parasitism on both natal and nonnatal hosts, whereas the foxglove population only performed well on its natal host, with low levels of parasitism on pea aphids. Although this pattern suggests a genetic basis for parasitism, the large difference in the two parasitoids’ ability to parasitize pea aphids, and the levels of parasitism in general, may also be influenced by nongenetic components. For instance, parasitism is most likely influenced by the extent of phenotypic plasticity exhibited by parasitoids developing in different host species. This includes host fidelity or morphological variables such as adult body size that are primarily environmentally determined (i.e., induced by developing in a host species), which can have a strong influence on the willingness to utilize a host species or the ability to overcome host defenses (Henry et al. 2008). Parasitoids from the foxglove population are, on average, half the size of parasitoids that have developed in pea aphids due to growth restrictions imposed by the size of the host species, which can influence oviposition success when attacking large aggressive host species such as the pea aphid (Henry et al. 2006). Although this may partially account for the low levels of pea aphid parasitism from foxglove aphid parasitoids, it does not account for the foxglove parasitoids outperforming pea aphid parasitoids on their natal host species, which supports the hypothesis of local adaptation. Offspring emergence showed significant variation between the two parasitoid populations, which supports the theory of genetic differentiation in the ability to successfully develop in a host. However, this pattern does not support local host species adaptation, in that parasitoids from the pea aphid population had higher offspring emergence on both host species (Fig. 1B). The host populations these parasitoids were collected from may account for this deviation in that they differed in the composition and availability of host species in their local environment. Parasitoids from the alfalfa field most likely did not have access to alternate host species, as the pea aphid was the only host species found in the field, whereas parasitoids from the potato field had several different host species to choose from. In an environment with the option of utilizing alternate host species, parasitoids may be practicing host switching, which is thought to inherently destabilize specialization through the obliteration of locally adapted gene pools (Kawecki and Ebert 2004). The aphids themselves may have also experienced different degrees of selective pressures from parasitism. Foxglove aphids may have experienced a refuge from parasitism due to the presence FIG. 3. The relationship between sisters in their ability to parasitize foxglove and pea aphids. Families emerging from (A) foxglove aphids and (B) pea aphids are presented separately. Each point represents one family of four sisters, with the mean value of two sisters assayed on pea aphids (y-axis) and the mean value of two sisters assayed on foxglove aphids (x-axis) making up each point. 248 LEE M. HENRY ET AL. of alternate hosts, where as pea aphids are more likely to have been exposed to greater selective pressures from Aphidius ervi, resulting in a more highly evolved defensive system (such as an increase in the frequency of endosymbionts that confer resistance to parasitism [Oliver et al. 2005]), which may partially explain the lower levels of parasitism and emergence from pea aphids in general. Further research is required to determine the effects of alternate host species on parasitoid specialization and local host adaptation. Local host adaptation in natural populations of parasitoids utilizing different host species is not uncommon (e.g., Vaughn and Antolin 1998, Althoff and Thompson 2001, Morehead et al. 2001, Hayward and Stone 2006, Stireman et al. 2006). Antolin et al. (2006) found that Diaeretiella rapae from two adjacent fields containing Russian wheat aphids (Diuaphis noxia) and cabbage aphids (Brevicoryne brassicae) were genetically differentiated and locally adapted by host species. Similarly, changes in Microctonus hyperdoae biotype frequencies introduced to New Zealand for control of the weevil Listronotus bonariensis were consistent with strong directional selection, providing one of the first clear demonstrations of adaptive evolution improving success rates of biological control introductions (Winder et al. 2003, Philips et al. 2008). These studies highlight the importance of source populations and natural genetic variation in natural enemy populations that are used in biological control of pests. Although sampling methods for detecting locally adapted populations have primarily focused on parasitoids for classical biological control introductions (Lozier et al. 2008), the techniques have clear applications for selecting the highest-quality source populations for the mass rearing of parasitoids to be released in agriculture. Heritability of fitness-related traits Knowing the heritability of life history traits is necessary for a mechanistic understanding of evolutionary processes. Results of the parent 3 offspring regression suggest there is significant heritable genetic variation in the capacity to parasitize a patch of aphids when assayed on both foxglove and pea aphids independently (Fig. 2A, B), indicating that this trait has a strong genetic component and that the genetic basis of parasitism is universally expressed, irrespective of host species. Heritability of parasitism on pea aphids (h2 ¼ 0.75) was lower than on foxglove aphids (h2 ¼ 0.95), which is not surprising, as the original population of parasitoids was collected from pea aphids, and selection should act to reduce additive genetic variation within our sample population for performance on pea aphids (Fisher 1930, Mousseau and Roff 1987). However, both of these values are still considered to be moderately high, as heritability for life history traits generally averages around 0.25 (Roff 1992). This suggests that genes involved in pea aphid parasitism have not reached fixation from our sample populations, Ecological Applications Vol. 20, No. 1 which is interesting given that the pea aphid was the only aphid species collected from this study site. This could result from interspecific, frequency-dependent selection or migrant individuals from alternate host species or alternate host patches with differing genotypes for resistance (Henter 1995, Henter and Via 1995). Perhaps even more interesting is the high heritability of parasitism on foxglove aphids from individuals collected from the pea aphid population (Fig. 2B), which suggests that a significant amount of standing genetic variation exists within this population for the ability to parasitize foxglove aphids. No trait heritability was detected in the emergence of offspring from mummies or in the sex ratio of offspring, indicating that these traits may be primarily determined by environmental conditions, have reached allele fixation, or may be solely influenced by maternal effects. The relationship between sisters assayed on the two different host species allowed us to investigate the influence of the environment (i.e., host species) on trait expression, using closely related individuals, with little maternal influence, as families emerged from the same host species. Results indicate that developing in different host species influences gene expression in that sister’s traits were either negatively correlated or had no detectable correlation. A strong negative relationship was detected in parasitism between sisters assayed on the two host species (Fig. 3B), when the families emerged from pea aphids. This negative fitness correlation indicates that a trade-off exists in the ability to successfully parasitize both host species, which suggests an antagonistic interaction between one or more genes. However, when parasitoids were reared on foxglove aphids, no significant relationship was detected in parasitism between sisters (Fig. 3A). One possible explanation for this deviation in the relationship between sisters when reared on different hosts is that parasitoids emerging from foxglove aphids are relatively small; previous research has shown that foxglove-reared parasitoids are limited in their ability to handle and successfully ovisposit in large, well-defended hosts such as the pea aphids (Henry et al. 2006). Thus the morphological limitations from developing in foxglove aphids may have masked the actual relationship between sisters. Additionally, no relationship between sisters was detected in the emergence or sex ratio of offspring, supporting the earlier claims that these traits may be determined by a combination of factors. Our results support the research by Henry et al. (2008), in that the ability to parasitize a host appears to be genetically determined and strongly heritable, irrespective of the host species in which the parasitoids are developing. Identification of heritable traits in natural enemies used in biological control is an essential first step in the initiation of breeding programs. Although selectively breeding natural enemies is not a common practice by commercial producers of biological control agents, our results demonstrate the potential of artifi- January 2010 HOST-ADAPTED PARASITOIDS IN BIOCONTROL cially breeding for specific traits to increase the efficacy of parasitoids on key pest species. Furthermore, our results suggest a negative relationship between genotypes that indicates an inability of parasitoids to simultaneously maximize fitness on more than one host, which coincides with results of Henry et al. (2008). Previous research has demonstrated that there can be a physiological mechanism involved in overcoming host defenses and that this process may be under directional selection in certain host–parasitoid systems (Carton et al. 1989, Kraaijeveld et al. 2001). Our result calls into question the oversimplification of using generalist parasitoids to control multiple aphid species in greenhouses, as well as the common practice of rearing parasitoids on a host species that it is not implicitly used to control, such as the pea aphid. If success of biological control is partly based on the quality of the natural enemies (van Lenteren 2000), improving the performance of parasitoids by selective breeding has great potential to improve parasitoid efficacy, which in turn increases economical viability of biological control agents. Greenhouse performance of host-adapted parasitoids Previous research by Henry et al. (2008) demonstrated that a foxglove selection line dramatically increased their capacity to parasitize foxglove aphids in a controlled laboratory experiment. Although compelling, these results do not confirm the effectiveness of these parasitoids as a biological control agent of foxglove aphids in commercial greenhouses, as there are many unpredictable factors in greenhouses that may hamper parasitoid performance. Parasitoids from the foxglove selection line produced an average of 63% more mummies than the pea aphid selection line when assayed on foxglove aphids in the greenhouse experiment. This clearly demonstrates the potential of using host selection lines to increase the efficacy and consistency of parasitoids for problematic aphid pests in greenhouses. Increased performance of selected parasitoids occurs not only through a greater physiological virulence for overcoming host defenses but also by an increase in host fidelity (Henry et al. 2008). Host fidelity and host location are highly plastic traits in many parasitoid systems (Villagra et al. 2007). The predictive nature of these plastic responses has great potential in biological control by establishing fidelity for a host species prior to release, which increases the probability that the natural enemy population will become established through a reduction in emigration and an increased capacity to locate hosts (Dicke 1999). These results provide insight into a novel technique to increase the quality of biological control agents through selection designs. Artificial selection designs can also be extended to nonprey resources, such as preadapting a natural enemy to the spatial structure or temperature of the intended foraging environment. Ideally, reduction in the cost of biological control to growers makes it easier 249 and more economical to apply. The importance of increasing natural enemy efficiency is evident in the recent movement to breed plant varieties that facilitate the movement and response of natural enemies (van Lenteren 2000). Thus it seems a logical progression to develop the biological control agents themselves through discerning collections from source populations and careful breeding designs. However, the caveat of such an approach is that it not only requires greater communication and extensive collaboration of researchers with growers but also with the commercial suppliers of natural enemies themselves. ACKNOWLEDGMENTS The authors thank Agriculture Canada for use of their facilities. Thanks to the Roitberg lab for advice and support. We also thank NSERC and the BC Greenhouse Growers Association for funding. LITERATURE CITED Althoff, D. M., and J. N. Thompson. 2001. Geographic structure on the searching behaviour of a specialist parasitoid: combining molecular and behavioural approaches. Journal of Evolutionary Biology 14:406–417. Antolin, M. F., T. A. Bjorkstein, and T. T. Vaughn. 2006. Host-related fitness trade-offs in a presumed generalist parasitoid, Diaeretiella rapae (Hymenoptera: Aphidiidae). Ecological Entomology 31:242–254. Carton, Y., P. Capy, and A. J. Nappi. 1989. Genetic variability of host–parasite relationship traits: utilization of isofemale lines in a Drosophila simulans parasitic wasp. Genetics, Selection, Evolution 21:437–446. Croft, P., J. Fenlon, R. J. Jacobson, and J. Dubas. 1999. Effect of tomato conditioning on Phytoseiulus persimilis AthiasHenriot (Acari: Phytoseiidae) population growth. Bulletin OILB/SROP 22:45–48. Cuartero, J., H. Laterrot, and J. C. van Lenteren. 1999. Hostplant resistance to pathogens and arthropod pests. Pages 124–138 in R. Albajes, M. L. Gullino, and J. C. van Lenteren, editors. Integrated pest and disease management in greenhouse crops. Kluwer Publishers, Dordrecht, The Netherlands. Dicke, M. 1999. Direct and indirect effects of plants on beneficial organisms. Pages 105–153 in J. R. Ruberson, editor. Handbook of pest management. Marcel Dekker, New York, New York, USA. Falconer, D. S., and T. F. Mackay. 1989. Introduction to quantitative genetics. Longman Group, Harlow, UK. Fisher, R. A. 1930. The genetical theory of natural selection. Clarendon Press, Oxford, UK. Force, D. C. 1967. Genetics in the colonization of natural enemies for biological control. Annals of the Entomological Society of America 60:722–729. Fox, L. R., and P. A. Morrow. 1981. Specialization: species property or local phenomenon? Science 211:887–893. Hayward, A., and G. N. Stone. 2006. Comparative phylogeography across two trophic levels: the oak gall wasp Andricus kollari and its chalcid parasitoid Megastigmus stigmatizans. Molecular Ecology 15:479–489. Henry, L. M., B. D. Roitberg, and D. R. Gillespie. 2006. Covariance of phenotypically plastic traits induces an adaptive shift in host selection behaviour. Proceedings of the Royal Society B 273:2893–2899. Henry, L. M., B. D. Roitberg, and D. R. Gillespie. 2008. Hostrange evolution in Aphidius parasitoids: fidelity, virulence and fitness trade-offs on an ancestral host. Evolution 62:689– 699. 250 LEE M. HENRY ET AL. Henter, H. J. 1995. The potential for coevolution in a host– parasitoid system. II. Genetic variation within a population of wasps in the ability to parasitize an aphid host. Evolution 49:439–445. Henter, H. J., and S. Via. 1995. The potential for coevolution in a host–parasitoid system. I. Genetic variation within an aphid population in susceptibility to a parasitic wasp. Evolution 49:427–438. Holt, R. D., and M. E. Hochberg. 1997. When is biological control evolutionarily stable? Ecology 78:1673–1683. Hopper, K. R., R. T. Roush, and W. Powell. 1993. Management of genetics of biological-control introductions. Annual Review of Entomology 38:27–51. Hufbauer, R. A. 2002. Evidence for nonadaptive evolution in parasitoid virulence following a biological control introduction. Ecological Applications 12:66–78. Hufbauer, R. A., and G. K. Roderick. 2005. Microevolution in biological control: mechanisms, patterns, and processes. Biological Control 35:227–239. Jervis, M. A. 1997. Parasitoids as limiting and selective factors: can biological control be evolutionarily stable? Trends in Ecology and Evolution 12:378–379. Kawecki, T. J., and D. Ebert. 2004. Conceptual issues in local adaptation. Ecology Letters 7:1225–1241. Kraaijeveld, A. R., K. A. Hutcheson, E. C. Limentani, and H. C. J. Godfray. 2001. Costs of counterdefenses to host resistance in a parasitoid of Drosophila. Evolution 55:1815– 1821. Lemasurier, A. D., and J. K. Waage. 1993. A comparison of attack rates in a natal and an introduced population of the parasitoid Cotesia glomerata. Biocontrol Science and Technology 3:467–474. Lozier, J. D., G. K. Roderick, and N. J. Mills. 2008. Evolutionarily significant units in natural enemies: identifying regional populations of Aphidius transcaspicus (Hymenoptera: Braconidae) for use in biological control of mealy plum aphid. Biological Control 46:532–541. Messenger, P. S., and R. van den Bosch. 1971. The adaptability of introduced biological agents. Pages 68–92 in C. B. Huffacker, editor. Biological control. Plenum, New York, New York, USA. Morehead, S. A., J. Seger, D. H. Feener, Jr., and B. V. Brown. 2001. Evidence for a cryptic species complex in the ant parasitoid Apocephalus paraponerae (Diptera: Phoridae). Evolutionary Ecology Research 3:273–284. Mousseau, T. A., and D. A. Roff. 1987. Natural selection and the heritability of fitness components. Heredity 59:181–197. Oliver, K. M., N. A. Moran, and M. S. Hunter. 2005. Variation in resistance to parasitism in aphids is due to symbionts not host genotype. Proceedings of the National Academy of Sciences (USA) 102:12795–12800. Pennacchio, F., M. C. Digilio, E. Trembley, and A. Tranfaglia. 1994. Host recognition and acceptance behaviour in two aphid parasitoid species: Aphidius ervi and Aphidius microlophi (Hymenoptera: Braconidae). Bulletin of Entomological Research 84:57–64. Phillips, C. B., D. B. Baird, L. L. Lline, M. R. McNeill, J. R. Proffitt, S. L. Goldson, and J. M. Kean. 2008. East meets west: adaptive evolution of an insect introduced for biological control. Journal of Applied Ecology 45:948–956. Pike, K. S., P. Stary, T. Miller, D. Alison, L. Boydston, and G. Graf. 1999. Host range and habitats of the aphid parasitoid Diaeretiella rapae (Hymenoptera: Braconidae) in Washington State. Environmental Entomology 28:61–71. Ecological Applications Vol. 20, No. 1 Powell, W., and A. F. Wright. 1988. The abilities of the aphid parasitoids Aphidius ervi Haliday and A. rhopalosiphi De Stephani Perez (Hymenoptera: Braconidae) to transfer between different known host species and the implications for the use of alternate hosts in pest control strategies. Bulletin of Entomological Research 78:683–693. Remington, C. L. 1968. The population genetics of insect introductions. Annual Review of Entomology 13:425–426. Roff, D. A. 1992. The evolution of life histories: theory and analysis. Chapman and Hall, New York, New York, USA. Roush, R. T. 1990. Genetic considerations in the propagation of entomophagous species. Pages 373–387 in R. R. Baker and P. E. Dunn, editors. New directions in biological control. Liss, New York, New York, USA. Sanchez, J. A., F. Canovas, and A. Lacasa. 2007. Thresholds and management strategies for Aulacorthum solani (Hemiptera: Aphididae) in greenhouse pepper. Journal of Economic Entomology 100:123–130. SAS Institute. 2007. JMP. Version 7.0. SAS Institute, Cary, North Carolina, USA. Sequeira, R., and M. Mackauer. 1992. Nutritional ecology of an insect parasitoid association: the pea aphid Aphidius ervi system. Ecology 73:183–189. Smith, M. A., D. M. Wood, D. H. Janzen, W. Hallwachs, and P. D. N. Herbert. 2007. DNA barcodes affirm that 16 species of apparently generalist tropical parasitoid flies (Diptera, Tachinidae) are not all generalists. Proceedings of the National Academy of Sciences (USA) 104:4967–4972. Stireman, J. O., J. D. Nason, S. Heard, and J. M. Seehawer. 2006. Cascading host-associated genetic differentiation in parasitoids of phytophagous insects. Proceedings of the Royal Society B 273:523–530. van den Bosch, R. 1964. Encapsulation of the eggs of Bathyplectes curculionis (Thompson) (Hymenoptera: Ichneumonidae) in larvae of Hypera brunneipennis (Boheman) and Hypera positica (Glyllenhal) (Coleoptera: Curculionidae). Journal of Invertebrate Pathology 6:343–367. van Lenteren, J. C. 1997. Commercial mass production and pricing of organisms for biological control of pests in Europe. Biological Control 10:143–149. van Lenteren, J. C. 2000. A greenhouse without pesticides: fact or fantasy? Crop Protection 19:375–384. van Lenteren, J. C., L. Z. Hua, and J. W. Kamerman. 1995. The parasite–host relationship between Encarsia formosa (Hymenoptera: Aphelinidae) and Trialeurodes vaporariorum (Homoptera: Aleyrodidae). XXVI. Leaf hairs reduce the capacity of Encarsia to control greenhouse whitefly on cucumber. Journal of Applied Entomology 119:553–559. Vaughn, T. T., and M. F. Antolin. 1998. Population genetics of an opportunistic parasitoid in an agricultural landscape. Heredity 80:152–162. Villagra, C. A., F. Pennacchio, and H. M. Niemeyer. 2007. The effect of larval and early adult experience on behavioural plasticity of the aphid parasitoid Aphidius ervi (Hymenoptera, Braconidae, Aphidiinae). Naturwissenschaften 94:903– 910. Winder, L. M., C. B. Phillips, C. L. Williams, R. C. Cane, K. Paterson, C. L. Vink, and S. L. Goldson. 2003. PCR-based DNA analysis corroborates phenotypic evidence of transAndean variation in the South American parasitoid Microctonus hyperodae. Bulletin of Entomological Research 95: 289–298.
© Copyright 2026 Paperzz