PsycheVolume 2012 (2012), Article ID 424817, 11 pagesdoi:10.1155/2012/424817

Review Article

Biological Control of Solenopsis Fire Ants by Pseudacteon Parasitoids: Theory and Practice

Lloyd W. Morrison

Department of Biology, Missouri State University, 901 S. National Avenue, Springfield, MO 65897, USA

Received 25 August 2011; Accepted 20 October 2011

Academic Editor: Jean Paul Lachaud

Copyright © 2012 Lloyd W. Morrison. This is an open access article distributed under the Creative Commons Attribution License, which permits unrestricted use, distribution, and reproduction in any medium, provided the original work is properly cited.

Abstract.

Pseudacteon parasitoids are potential biocontrol agents of invasive Solenopsis fire ants. Pseudacteon species that parasitize the invasive S. invicta Buren and S. richteri Forel have been introduced to, and naturally dispersed across, the southeastern USA, although there is no evidence yet that Solenopsis host ant populations have decreased. The ability of introduced Pseudacteon species to regulate Solenopsis populations will depend upon the relative importance of top-down effects in the recipient communities. In this paper, I examine the characteristics of the Pseudacteon/Solenopsis parasitoid/host system and evaluate the extent to which research findings are consistent with top-down control. Laboratory and field experiments evaluating Solenopsis population regulation have been equivocal, and overall the available evidence provides little support for strong top-down effects in this system. Competitive exclusion may occur among introduced Pseudacteon species, and future efforts at biological control are likely to be more efficacious if they focus on other types of natural enemies.

1. Introduction

Many species of Pseudacteon (Diptera: Phoridae) are parasitoids of Solenopsis (Hymenoptera: Formicidae) fire ants. Several species of Solenopsis fire ants are invasive pests and others have the potential to be [1]. High densities of the invasive S. invicta Buren in North America are usually attributed to an escape from natural enemies [2]. Much recent research has focused on the potential use of Pseudacteon parasitoids as classical biological control agents to regulate Solenopsis fire ant populations, particularly S. invicta and S. richteri Forel in North America. Two South American Pseudacteon species—P. tricuspis Borgmeier and P. curvatus Borgmeier—have been released at multiple locations and dispersed naturally across the southeastern USA. It is estimated that P. tricuspis now occurs in 65%, while P. curvatus may occur in as much as 90% of the invasive S. invicta/S. richteri range [3]. Two other species—P. litoralis Borgmeier and P. obtusus Borgmeier—have been established in localized areas, P. cultellatus Borgmeier has been recently released in Florida, and releases of additional species are planned [3, 4]. In addition to the direct effect of mortality, Pseudacteon phorids may have indirect effects on their Solenopsis hosts, affecting their behavior and potentially putting the host species at a relative disadvantage with competing ants [5].

There have been many studies conducted on various aspects of the Pseudacteon/Solenopsis parasitoid/host system, and the literature is in need of an objective, critical review. There is great interest in whether the introduction of Pseudacteon phorids can regulate invasive fire ant populations, and if so, to what degree. I conducted original research on this system for a decade, but have more recently pursued other avenues of study. The success or failure (perceived or actual) of this biological control program has no bearing on my obtaining funding, promotion, or tenure. Thus, I am in a good position to conduct a knowledgeable, yet detached review. I do not attempt to review all the Pseudacteon/Solenopsis literature, but focus on the potential of introduced Pseudacteon parasitoids from South America to regulate population densities of host Solenopsis ants in their invasive range in North America, through both direct and indirect effects.

2. The Species

2.1. The Host

The genus Solenopsis contains about 185 described species worldwide; the ~20 Solenopsis species known as “fire ants” are all native to the new world [1]. Three of these fire ants are invasive pests: S. invicta, the most notorious, is native to South America but has invaded North America, the Caribbean, Australia, Taiwan, and China [6]. S. richteri, also native to South America, has invaded the southeastern USA, where it has hybridized with S. invicta [7]. S. geminata (Fabricius), whose natural range spans southern North America to northern South America, has been found at numerous low latitude sites around the globe [7]. The vast majority of Solenopsis fire ant research has focused on these three species. All three are characterized by polymorphic workers, which live between 2 and 8 months, depending on worker size and temperature [8]. The massive fire ant literature has been summarized by Taber [7] and synthesized by Tschinkel [1].

One important aspect of Solenopsis biology that is relevant here is the seasonal cycle of population abundance. In the southeastern USA, S. invicta reaches peak abundances in midwinter, and the lowest worker numbers occurring in midsummer are only about half that of winter highs [9]. S. invicta above ground foraging activity is highest in summer, however, and lowest in winter when soil temperatures are too cold to forage [10, 11]. Thus, the availability of hosts to Pseudacteon parasitoids is greatest in the summer months, even though S. invicta absolute densities are near their lowest.

Beyond the seasonal oscillations in abundance, Solenopsis population size may vary with other factors. The Solenopsis species in question are disturbed habitat specialists [1, 12]. Disturbances come in all degrees, however, and across a broad scale either too much or too little disturbance may result in lower fire ant abundances [13]. Disturbance regimes undoubtedly vary temporally and result in variability in Solenopsis populations. Climatic events (i.e., droughts, floods, and unusually cold weather) may also affect Solenopsis abundances [14, 15]. Fluctuations in abundance due to a variable disturbance regime or such climatic events could either amplify or dampen the inherent seasonal oscillations.

Finally, Solenopsis fire ants have the propensity to rapidly increase in abundance. After removing all S. invicta from experimental plots in Florida, for example, S. invicta recolonized the plots and in only two years reached abundances similar to control plots [16]. It is against this background of wide and potentially variable fluctuations in host population size, in addition to a strong potential for colony growth, that the regulatory effect of Pseudacteon parasitoids must be evaluated.

2.2. The Parasitoid

Although a number of taxonomic issues remained unresolved, over 20 Pseudacteon species are known to parasitize Solenopsis saevissima complex fire ants in South America [17]. Similarly, more than 20 Pseudacteon species parasitize Solenopsis geminata complex fire ants from North America to northern South America [18]. The basic biology and natural history of Pseudacteon phorids that parasitize Solenopsis fire ants have been summarized by Porter [19] and Morrison [20]. The life cycle of Pseudacteon, in brief, is as follows. A female Pseudacteon hovers near Solenopsis worker ants and inserts eggs into the thorax of hosts in aerial attacks with a specialized ovipositor. Three larval instars—the second of which migrates to the head—precede pupation. At pupariation, the worker is killed by the parasitoid consuming all the tissue inside the head capsule, which is then used as a pupal case. Development from egg to adult takes from 5 to 12 weeks, depending upon temperature and the Pseudacteon species. Pseudacteon are solitary parasitoids, with only one larva able to complete development in each host. Each female Pseudacteon, however, may produce >200 eggs [21].

3. Theory

Whether or not Pseudacteon parasitoids control or regulate population densities of Solenopsis fire ants can be thought of as a function of the relative importance of top-down versus bottom-up effects in the communities in question. In food web terminology, bottom-up effects occur when the abundance of a resource affects the population of the consumer of that resource. The higher the abundance of resources at lower trophic levels, the higher the abundance or diversity that can be obtained at higher trophic levels. Top-down effects, on the other hand, occur when the population density of a consumer affects the abundance of its resource. Top-down control refers to the situation where the abundance or diversity of lower trophic levels is dependent on effects from consumers at higher trophic levels [22]. There has been much discussion in the literature over the relative importance of top-down versus bottom-up effects in arthropod communities, including the seasonal and spatial variability in such effects [23–29].

In a community with strong top-down effects, Solenopsis populations would be regulated by Pseudacteon parasitoids (or other predators or parasites). In contrast, in a community with strong bottom-up effects, Solenopsis populations would ultimately be regulated by the food resources available to them, and simply support Pseudacteon populations but not be controlled by them. Larger Solenopsis populations could support larger Pseudacteon populations. Obviously, biological control of host ants requires a system with relatively strong (and consistent) top-down effects.

Interspecific competition has traditionally been viewed as the primary mechanism organizing ant communities and limiting ant populations [30]. It has been suggested, however, that top-down processes such as parasitism may also play an important role in some ant communities [31]. Here, I make no attempt to evaluate the importance of parasitoids to ant communities in general, but rather to determine which characteristics of the Pseudacteon/Solenopsis parasitoid/host system are consistent with top-down control. I refer to the prevalence of such top-down effects as “strong control,” in reference to the goal of regulating invasive Solenopsis populations.

The relative importance of top-down effects can be illustrated by comparing two scenarios: in the first scenario—“strong control”—top-down effects prevail. This scenario is characterized by (1) a diversity of Pseudacteon species that exert a broad range of parasitism pressure on host Solenopsis ants, (2) consistently high abundance and activity of Pseudacteon, (3) high rates of mortality resulting from parasitism, (4) a lack of refuge for, or ability to behaviorally adapt in, host ants, and (5) shifting of the outcome of interspecific interactions with competing ants. The second scenario, which I term “weak control”, is characterized by (1) low diversities of Pseudacteon species, (2) low or fluctuating abundance or activity of Pseudacteon, (3) low rates of mortality resulting from parasitism, (4) the presence of a refuge or the ability to behaviorally adapt by host ants, and (5) little or no effect on the outcome of interspecific interactions with competing ants.

These two scenarios more appropriately represent the ends of a continuum rather than two mutually exclusive states (or because multiple characteristics are involved, the margins of a multidimensional space). Moreover, the characteristics of each scenario are largely independent of each other. Evaluation of recent research results relative to these scenarios allows for a greater understanding of the degree to which Pseudacteon parasitoids may control or regulate population densities of Solenopsis fire ants.

Given the high background population fluctuations of host Solenopsis, the potential effects of Pseudacteon as described in the two scenarios above are illustrated as a conceptual model in Figure 1. In the strong control scenario (Figure 1(a)), broad parasitism pressure (direct and indirect) depresses fire ant populations consistently over time, resulting in peaks and troughs of fire ant population cycles that are lower than without the parasitoids. The mean Solenopsis abundance over time is also lower.

(a)

(b)

Figure 1: Two hypothetical scenarios of the potential effects of introduced Pseudacteon parasitoids on Solenopsis fire ant populations. (a) Strong control: parasitism pressure depresses fire ant populations consistently over time, resulting in peaks and troughs of fire ant population cycles that are lower than without the parasitoids. (b) Weak control: parasitism pressure primarily affects host ant populations seasonally, or to an otherwise relatively small extent, and ants rebound under optimum growth conditions. (Shaded areas indicate the amount of decrease due to the parasitoids.)

In the weak control scenario (Figure 1(b)), parasitism pressure is weak and may only affect host ant populations seasonally, or is otherwise greatly limited in intensity. Pseudacteon populations also fluctuate, reaching their highest abundances and thus exerting peak parasitism pressure in the fall, due to greater host availability in the summer (because of higher above-ground foraging activity by the ants). Because of low rates of mortality due to parasitism and the ability of ants to adapt behaviorally and lessen the indirect effects, colony fitness is only slightly affected, and this decrease comes at a time when overall colony size is peaking. Because of the overall cyclical nature of Solenopsis abundance and the added stochastic effects of disturbance and climate (depicted in this figure as irregular seasonal oscillations), the impacts of Pseudacteon may be relatively small. Over the long term, such effects may be washed out by the greater population variability due to other factors. Under optimum disturbance intensity and climatic conditions, host ants may regain previous population peaks. In this scenario, the long-term average Solenopsis abundance or range of fluctuations may change relatively little due to Pseudacteon.

4. The Evidence

4.1. Diversity of Pseudacteon Species

In most locations that have been studied, multiple Pseudacteon species have been found. This is true for Solenopsis saevissima complex fire ants in South America and Solenopsis geminata complex fire ants in North America [17, 32–35]. Host ants are partitioned among Pseudacteon species along several axes, including size of worker [36–38], host location preferences [33, 39], and time of day [35–40]. Thus multiple Pseudacteon species attack a greater size range of workers, engaged in a wider diversity of activities, over a longer period of time than a single Pseudacteon species would.

Although multiple Pseudacteon species may cooccur at a site, most species are usually relatively rare. This is also true both in North America [5, 34] and South America [32, 33, 35, 41–43]. The niche segregation observed is likely the result of competition among Pseudacteon species for hosts. There is now evidence that introduced South American Pseudacteon species are competitively displacing each other in North America [4, 44, 45], and a reanalyses of abundance data from South America suggests competitive exclusion exists there as well [44].

4.2. Abundance and Activity of Pseudacteon Species

Adult Pseudacteon live for only a few days [46], and reveal relatively great variability in abundance over time [34, 41, 47–49]. In tropical and subtropical climates, Pseudacteon species are active year round, although relative abundance varies seasonally [32, 35, 41, 49]. Pseudacteon species are active from dawn to dusk, but diel variation exists among species [35]. In more temperate zones, flight activity of Pseudacteon is limited by cool air temperatures and adults may not be active in the winter months [34].

Introduced P. tricuspis populations in the southeastern USA reveal cyclical patterns of seasonal abundance, with peaks in the fall and troughs in the spring [48, 50, 51]. Solenopsis above ground foraging activity, and thus host availability is highest in summer. Thus P. tricuspis densities track host ant availability (with some lag time to be expected based on the 5–12-week-long development cycle) and greater availability of hosts (i.e., resources) is correlated with higher parasitoid (i.e., consumer) populations. Abundance patterns of P. curvatus, however, may differ, at least in some areas [S. D. Porter, unpublished data].

4.3. Mortality due to Parasitism

Parasitism rates (i.e., the percentage of Solenopsis workers in a colony infected with a Pseudacteon egg or larva at a given point in time) have been reported to be very low in a number of studies. In Texas, S. geminata—hosts of native North American Pseudacteon species—had parasitism rates of <3% [36]. Parasitism rates of Solenopsis invicta in its native range in Argentina by native South American Pseudacteon species were similarly <3% [35]. Parasitism rates of Solenopsis invicta in its exotic range in Florida from introduced Pseudacteon are generally ≤2% [48, 52]. These observed rates are an order of magnitude below the lowest parasitism rates associated with successful biological control programs (>30%) [53, 54]. These rates for successful biocontrol for other types of parasites, however, are based on the direct effect of mortality only.

Workers that are parasitized by Pseudacteon are not a random assortment from the colony, but rather represent primarily older ants with a shorter life expectancy. Fire ants exhibit a division of labor, in which the particular task engaged in by a worker depends on the age and size of that worker. In general, younger workers engage in relatively safe activities within the central colony, whereas older workers are found near the periphery of the nest, and the oldest workers engage in the most dangerous activity: foraging [55]. Mortality rates of foragers may be as high as 5% per day [1]. Because of the high mortality rates associated with foraging activities in ants in general, foragers have been described as a “disposable caste” [56].

Pseudacteon phorids attack host workers involved in foraging, interspecific interactions, and colony defense—all relatively dangerous activities. Thus most of the workers parasitized are engaged in high-risk activities and near the end of their natural lives, and colony fitness is affected to a lesser degree than if workers were parasitized at random with respect to age.

4.4. Host Ant Refuges and Behavioral Adaptations

A primary focus for research into the indirect effects of Pseudacteon has been the reduction of foraging in host ants in the presence of these parasitoids. A number of studies involving different Pseudacteon/Solenopsis combinations in both North and South America have revealed that in the presence of these parasitoids, worker behavior changed and foraging at rich food resources dramatically diminished [5, 57–61]. The size of foraging Solenopsis workers has also been observed to decrease in the presence of Pseudacteon [52–64]. These studies, however, have almost exclusively focused on short-term effects of phorids at rich food resources, characterized by the recruitment of many workers in the absence of any shelter or refuge for the host workers and during ideal conditions for Pseudacteon flight activity.

Yet foraging in these Solenopsis species occurs under a great variety of conditions. In other words, these ants are characterized by a relatively broad foraging niche (sensu, [65]). They may forage by day or night [5, 66], as long as the soil temperature is at least 15°C [10, 11]. Solenopsis fire ants are omnivorous, with a very catholic diet [67, 68]. They excavate elaborate underground tunnel systems [69], and some unknown proportion of their food may be derived from underground sources (i.e., plant roots or root homopterans) [67]. The range of food items and types varies greatly; they may retrieve small items individually, but many workers may recruit to larger or long-lasting resources.

In contrast, Pseudacteon flies are not active after dark. Their aerial mode of attack makes it impossible to attack workers in underground tunnels (worker ants will quickly kill Pseudacteon flies if they can catch them). Additionally, Pseudacteon are unlikely to affect foraging of items that can be retrieved individually, although this has not been carefully studied. Some Pseudacteon species may not even affect foraging of relatively rich food resources if these are uncontested. Introduced P. tricuspis in North America, for example, were not attracted to workers foraging at such resources, unless involved in interspecific interactions with other ants [39]. P. tricuspis is attracted to the alarm pheromones and venom alkaloids that are typically released in such interactions [70, 71].

Pseudacteon native to North America are not active when air temperatures drop below 20°C [34], although some species in South America are active down to 14°C [41]. Thus there may be a narrow temperature zone in which it is warm enough for above-ground Solenopsis foraging, but not for Pseudacteon activity, although this appears to vary geographically and by species. Thus, Pseudacteon phorids will affect some unknown fraction of the overall broad spatiotemporal foraging niche of Solenopsis.

Furthermore, although the reduction in food obtained from such rich food resources may appear very large in the short term, in the longer term Solenopsis ants may be able to adapt behaviorally and still obtain much of the resource in question, if not removed by competitors. Field studies have shown that although forager numbers may decrease, Solenopsis workers do not usually completely abandon food resources in the presence of Pseudacteon, but some workers remain behind to guard the resource [34, 47, 59]. Foraging has even been observed to rebound to earlier levels after a depression by Pseudacteon [33]. Workers have been observed tunneling beneath a rich food source and covering it with dirt and debris [5, 47].

Although most laboratory studies have constrained foraging to occur only in the presence of Pseudacteon, the design of one laboratory study allowed a colony of S. invicta to forage simultaneously in one arena with P. tricuspis and in a second arena without the parasitoid. Although less food was retrieved from the arena with P. tricuspis, the sum of food obtained from both foraging arenas was not different from that obtained in control trials without parasitoids [61]. Thus the colonies were able to compensate for decreased food retrieval caused by P. tricuspis harassment by simultaneously increasing food consumption when food was available elsewhere.

4.5. Effects on Interspecific Interactions

Pseudacteon species were never expected to have large direct effects of mortality on Solenopsis ants, and the expectation of this parasitoid’s ability to regulate host ant populations was based primarily on the indirect effect on host behavior. These short-term behavioral effects would mean relatively little to colony fitness if they merely represented a delay in obtaining food resources. If, however, other ant species are able to secure a competitive advantage due to Solenopsis’ parasitoid evasion behavior and are able to obtain relatively more food resources, then Pseudacteon could play an important role in mediating overall ant community dynamics and species abundance relationships.

Orr et al. [60], working in South America, observed S. invicta to lose food resources to competing ants in the presence of Pseudacteon phorids. Other studies, however, have found that host Solenopsis workers under Pseudacteon attack often did not lose control of the resource to competing ants. Studies of Pseudacteon parasitoids specific to S. geminata in Texas revealed that the presence of the parasitoids had no effect on the outcome of interspecific interactions involving S. geminata [5, 47]. A comparative study in Brazil revealed that S. invicta-specific Pseudacteon had no effect on the outcome of interspecific competition between S. invicta and other ants at two of three sites [72]. Thus, based on the available evidence, the ability of parasitoids to affect the outcome of interference competition among ant species appears to be too weak to be scientifically documented in many communities.

5. Long-Term Experiments

5.1. Laboratory Experiments

It has proven difficult to provide evidence for the success (or failure) of introduced Pseudacteon species in regulating host Solenopsis ants at the population level. Most evidence for a Pseudacteon effect, as discussed above, comes from short-term behavioral studies (minutes to hours in duration). In a relatively long-term lab study (28 days) incorporating both Pseudacteon phorids and a competing ant, Forelius pruinosus (Roger), Mottern et al. [73] reported a reduction in foraging in S. invicta due to Pseudacteon harassment, but no change in the colony growth rate of S. invicta. It is possible that the duration of this experiment was too short, or the method used to measure colony growth (i.e., photographing brood piles) was not precise enough. The most likely explanation, however, is that ants were allowed to forage beyond the period that Pseudacteon attacked, and Solenopsis was able to compensate by increasing food retrieval when Pseudacteon were not active. Mottern et al. [73] state that such conditions would be “representative of those found in nature.” No change in the growth rate of the competing ant was observed either, although this was not surprising because F. pruinosus never entered the communal foraging chamber.

In a longer lab study (50 days), Mehdiabadi and Gilbert [74] documented that the reduction of foraging in S. invicta due to Pseudacteon harassment did, as expected, eventually result in reduced colony fitness. In that study, the presence of P. tricuspis reduced the abundance of middle-sized workers, but not small-or large-sized workers. Worker ants, however, were always constrained to forage in small trays for limited periods in the presence of P. tricuspis, without any refuge or potential to adapt their foraging behavior. It is noteworthy that a combination of P. tricuspis phorids and a competing ant—this time Forelius mccooki (McCook)—had no greater effect on colony fitness than the competing ant alone [74]. As in the Mottern et al. [73] study, no increase was observed in the reproductive output of the competing ant [75]. (Interestingly, Mottern et al. [73] criticized the statistical analysis of Mehdiabadi and Gilbert [74], claiming that no significant differences existed for any of their treatments!)

Thus, the ambiguous results of these laboratory experiments provide little empirical support for the idea that Pseudacteon phorids could mediate competitive interactions that would ultimately lead to a decrease in Solenopsis populations, while allowing for a relative increase in competing ant populations. The general problem with such laboratory experiments is that the design can greatly influence the outcome. Given the complexity of fire ant foraging and the multitude of interactions with other species, any community-level laboratory experiment is destined to be an oversimplification of the natural world with limited inference.

5.2. Field Experiments

Field experiments, while more realistic, have their own limitations, in this case primarily logistical. Fire ant populations are undoubtedly affected by many factors, and while many of these variables can be controlled for in the laboratory, attempting to isolate the effect of one factor in the context of a broad field experiment is very difficult. Moreover, introduced Pseudacteon species spread naturally at a rapid rate; P. tricuspis dispersed at rates of up to 30 km/year for the first few years after establishment in north Florida [76], and at rates of up to 57 km/year over the following four years [77]. After three and a half years, P. curvatus had dispersed even farther in Florida than P. tricuspis did over the same period after initial release [78]. In Texas, small satellite populations of P. tricuspis have been found tens of km beyond the main expansion front; this jump dispersal was probably assisted by the prevailing winds [79].

Thus it is difficult to have true control sites that are not colonized within the time course of an experiment. Control sites would have to be placed so far away that there could be systematic differences in environmental variables between the treatment and control sites. This is almost a moot point, as by now the vast majority of the invasive range of Solenopsis in the southeastern USA is estimated to have been colonized by at least one introduced Pseudacteon species [3]. Because of the tiny size of Pseudacteon, it is impractical to attempt to construct enclosures or exclosures, as these would include or exclude almost all other species (except microscopic ones).

The only published field experiment—including control plots (albeit 2 counties away) and spanning relatively large spatiotemporal dimensions—failed to find any measurable effect of introduced P. tricuspis on S. invicta in Florida [50]. The study was ended after 3 years when P. tricuspis dispersed to control plots. Relatively large variabilities were observed in fire ant activity and abundance, however, in both treatment and control plots. Thus the effects of this parasitoid would have had to be relatively large (perhaps reducing host ants by as much as 30%) to be detectable [50].

Studies are underway to gauge impact by comparing fire ant abundances before and after the introduction of Pseudacteon, in the absence of any control sites [3]. Such comparisons could be misleading, however, and should be interpreted with extreme caution. Fire ant abundances can and do change in response to many factors. S. invicta abundance, for example, was found to decrease by almost an order of magnitude over 12 years at a Central Texas site [80]. Pseudacteon species had not become established in Central Texas at the time, although other natural enemies of fire ants were present [80]. Additionally, numerous pathogens of Solenopsis fire ants are now known to be present in North America, and many have relatively high infection rates [52, 81, 82]. Finally, broad scale trends (i.e., climate cycles or directional change) may affect fire ant abundances independently of parasitoids.

6. Synthesis

6.1. Summary of the Evidence in Relation to Theory

Multiple Pseudacteon species frequently cooccur, although usually only one or a few species are very abundant. Overall, the Pseudacteon assemblage present at a given location may reach relatively high abundances at times, although populations fluctuate, and in the case of the introduced P. tricuspis in Florida, in synchrony with host availability. Parasitism rates are usually very low, and most workers parasitized are probably near the end of their natural lives, so this direct effect of parasitism may be almost negligible. Host ants may engage in much of their foraging in the absence of Pseudacteon flies and have the ability to adapt their behavior in the presence of this parasitoid, so that in the long term, the overall reduction in resource retrieval is likely much less than that suggested in short-term observations. Finally, Solenopsis species often do not lose control of rich food resources to competing ants in the presence of Pseudacteon.

Thus the available evidence suggests that any impacts of Pseudacteon phorids on host ant populations are generally small, especially when measured over the relatively large population variability of Solenopsis fire ants. Moreover, given the ability of Solenopsis to rapidly increase in population size under ideal conditions, any depression in Solenopsis populations by Pseudacteon phorids could be ephemeral if parasitism pressure is not consistent. Thus, the effects are probably much closer to the “weak control” scenario described above, although such effects could vary geographically and temporally. Experimental assessments of the impact of introduced Pseudacteon species have been few, and the results equivocal, although certainly no large impacts have been documented with any scientific rigor. Unfortunately, due to the constraints described above, we may never have a reliable, precise estimate for the effect of Pseudacteon parasitoids on Solenopsis fire ant populations in nature.

Thus the available evidence provides little support for strong top-down effects in this system. The accumulated data reveal that introduced P. tricuspis in North America are positively correlated with S. invicta availability, both temporally [48, 50, 51] and spatially [51]. These findings are not inconsistent with the hypothesis that larger Solenopsis fire ant populations simply support higher abundances of Pseudacteon parasitoids, and that Solenopsis populations are primarily regulated by other factors.

6.2. Host Specificity and Knowledge Gaps

Although Pseudacteon phorids may have relatively small effects on fire ant populations, they possess two very desirable qualities of a biocontrol agent. They have been documented to be highly host specific, in a battery of tests conducted: (1) in the field in South America [83, 84], (2) in the lab prior to the release of South American Pseudacteon species to North America [85–88], and (3) in the field in North America after the establishment of introduced populations [89, 90]. Thus, Pseudacteon phorids appear to be safe (i.e., no documented adverse effects on any other species), which is the most important quality of any biocontrol agent. Additionally, once established, Pseudacteon species will persist as a permanent component of communities in which host Solenopsis are found, and naturally disperse to others.

Several aspects of Pseudacteon/Solenopsis interactions need more study. Some Pseudacteon are attracted to mound disturbances [33, 39], although the potential effects of Pseudacteon on mound disturbances are less clear than those of interruption of foraging. The presence of Pseudacteon may delay the mound rebuilding process, but only for a matter of hours, until Pseudacteon activity ceases with darkness. The mound is important in regulating brood temperature and thus development [91], and movement of brood out of the mound due to disturbance and delayed reconstruction could adversely impact colony fitness, although such an effect seems ephemeral and thus relatively small. The frequency of natural mound disturbance events is an important variable in assessing this impact, and this disturbance regime no doubt varies geographically.

Morrison and King [39] found that numerous P. tricuspis flies were attracted to S. invicta mound disturbances when nonnestmate S. invicta were added, resulting in interspecific interactions, but on average fewer than one parasitoid was attracted in the absence of such interactions. Thus, most mound disturbances in the absence of interspecific interactions would probably be little affected by P. tricuspis, although other Pseudacteon species may differ in this aspect of their behavior. Pseudacteon are also attracted to Solenopsis mating flights [92]. Although Solenopsis reproductives are not suitable hosts [19], workers are very active on the mound surface before the reproductives take flight [93], and the presence of Pseudacteon could dampen this activity, potentially disrupting the mating flight. Large numbers of workers may be vulnerable to parasitism during mating flights or mound reconstruction, and such workers may be younger than workers engaged in foraging, thus representing a potential greater loss to overall colony fitness. Finally, Pseudacteon are carriers of pathogens that infect Solenopsis [94], although actual vectoring of diseases among colonies has not been demonstrated.

6.3. Implications and the Bigger Picture

Efforts are underway to introduce additional South American Pseudacteon species to North America. The question is how many additional species should be introduced? Because of the relatively high degree of niche partitioning observed in Pseudacteon species in South America, and the coexistence of multiple species at a site, the traditional wisdom has been that multiple Pseudacteon species will coexist at North American release sites, and that more Pseudacteon species will exert greater parasitism pressure on host Solenopsis ants. The species abundance patterns of Pseudacteon in both North and South America, and the recent, relatively unexpected finding of competitive exclusion among introduced Pseudacteon species, however, suggest only one or two introduced species may be abundant at any given location. Thus the introduction of additional Pseudacteon species may simply reduce the abundance of already-established species, without substantially increasing the density of the overall Pseudacteon assemblage.

An argument can be made that multiple Pseudacteon species are necessary because of the diversity in invasive Solenopsis populations in North America. Both S. invicta and S. richteri (and a hybrid) are present, and colonies may be either polygyne (i.e., multiple queen) or monogyne (i.e., single queen) [1]. There have been attempts to “match” or find the best combination of South American Pseudacteon species or biotypes with North American Solenopsis populations [95]. Ultimately, given the speed of dispersal of this parasitoid, after introductions of multiple Pseudacteon species to multiple locations in the Solenopsis invasive range, the flies may eventually sort themselves out. Not all Pseudacteon species may disperse at the same rate as P. tricuspis and P. curvatus, however. P. litoralis has spread much more slowly from a single release site in Alabama [4]. Although Pseudacteon species appear to have no detrimental effects, the time and effort involved in evaluating, rearing, and releasing these flies might be better spent evaluating other types of natural enemies. At this point, it seems likely that the marginal contribution of each additional Pseudacteon species released will be diminished as more species are added.

In South America, a diversity of parasites, pathogens, predators, and competitors affect S. invicta [1, 96]. Thus, introduction of a single type of natural enemy is unlikely to result in outsized reductions of invasive Solenopsis populations. It is more likely that regulation is incremental, and that each type of introduced natural enemy may have a relatively small effect, yet one that is cumulative so that overall control becomes greater with the addition of more types of natural enemies. Thus, the continued search, evaluation, and introduction of other safe (i.e., host-specific) natural enemies of Solenopsis fire ants may eventually lead to measurable levels of fire ant population regulation.

Given the general lack of evidence for strong top-down control in this system, it is possible that other ants represent the greatest natural enemies of Solenopsis. The South American ant fauna contains more species that are strong competitors of S. invicta than does the North American fauna [72, 97, 98]. Many of these ant species would have their own deleterious impacts to recipient biotas, perhaps even greater than Solenopsis fire ants, and introductions of such natural enemies are not seriously contemplated. If competition from other ants is the primary reason that S. invicta is less abundant in South America, it follows that introductions of all possible other types of natural enemies will not result in a decrease of North American S. invicta or S. richteri populations to South American levels.

The conventional wisdom of Pseudacteon biological control is that the presence of these parasitoids may shift the competitive balance away from Solenopsis fire ants to native ant species, allowing for a relative increase in abundance of the native species at the expense of the invasive Solenopsis. Recent work on the effects of disturbance, however, challenges the conventional wisdom that Solenopsis fire ants are strong competitors that have displaced native ants primarily due to a competitive asymmetry. King and Tschinkel [99] obtained experimental evidence suggesting that native ants are first displaced as a result of habitat disturbance, and then Solenopsis fire ants—which are disturbed habitat specialists—move into the disturbed areas. Experimentally removing S. invicta from disturbed areas did not result in an increase of native species [100]. In this study, conducted in forest habitat in Florida, “disturbance” resulted in the simplification of habitat structure to a type that was more similar to the habitat where S. invicta is native (i.e., open areas with high insolation). Thus, at least in some areas, disrupting the behavior of Solenopsis fire ants or even reducing their abundances may have limited effects on native ant diversity, in the absence of restoring disturbed or simplified habitats.

Habitat type or disturbance alone, however, cannot adequately explain the high abundances of invasive Solenopsis fire ants in North America. Solenopsis species were found to be more abundant at the same type of disturbed (i.e., roadside) sites in North America relative to South America [2]. Thus the abundance of Solenopsis fire ants in an area is likely the result of a number of factors (and interactions of factors), including habitat type, degree of habitat disturbance, and the presence of natural enemies. Ultimately, efforts to reduce invasive fire ant densities would probably benefit by taking a broad perspective and include attempts at habitat restoration in addition to the introduction of an array of natural enemies.

Acknowledgment

Sanford Porter made helpful comments on the paper.

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