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1 December 2008 Large size as an antipredator defense in an insect
Douglas W. Whitman, Shawn Vincent
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Abstract

Although large size is considered an evolved antipredator defense for some vertebrates and shellfish, large size is generally not considered an adaptive defensive trait in insects. Here we propose that large size in chemically defended grasshoppers has evolved as a beneficial antipredator trait. The lubber grasshoppers Romalea microptera and Taeniopoda eques are the largest grasshoppers in North America north of Mexico. These closely related species escape most vertebrate predation by possessing powerful predator-deterrent toxins and by nocturnal roosting. We hypothesize that escape from vertebrate predation allowed lubbers to evolve a larger body size, increased fecundity and provided many other benefits, including defense against invertebrate predators. To test the hypotheses that large lubber size reduces predation, we conducted feeding trials with wolf spiders (Honga carolinensis), assassin bugs (Arilus cristatus), preying mantids (Tenodera aridifolia), fire ants (Solenopsis invicta), frogs (Rana pipiens), and birds (Sturnus vulgaris and Passer domesticus). Our results show that larger lubber instars enjoyed a highly significant advantage vis-à-vis predators, demonstrating the adaptive value of large size against both vertebrate and invertebrate predators. Adult lubbers were generally immune from predation. It appears that lubbers have evolved to occupy a relatively predator-free ecological space: they are too large to be attacked by most invertebrate predators and too toxic for most vertebrate predators. We propose an evolutionary scenario whereby a change in feeding behavior toward vertebrate-toxic plants served as an evolutionary breakthrough, setting in motion the subsequent evolution of increased chemical defense and large body size in lubbers. To determine if large size is associated with chemical defense in grasshoppers in general, we compared body sizes of ~ 40 toxic vs ~ 3,000 nontoxic grasshopper species. Our results show that chemically defended species tend to be larger than nondefended grasshoppers, supporting an association between chemical defense and large size in insects. Large size may be favored in insects when vertebrate predation is removed as a strong selective factor.

Introduction

Insects have evolved an impressive arsenal of antipredator defenses, including, rapid escape, crypsis, anachoretes (hiding in holes), mechanical and chemical defenses, startle and threat behaviors, hard exoskeletons, mimicry, deimatic behavior, shelter-building, group and symbiotic defenses, and rapid reproduction, which out-paces that of associated predators (Edmunds 1974, Blum 1981, Evans & Schmidt 1990, Salazar & Whitman 2001). Small size is a key component of many of these defensive strategies. Small insect prey are less conspicuous to vertebrate predators than large prey and are often more difficult to catch. Small insects generally have faster population growth rates than larger insects, and vertebrate predators generally prefer larger insect prey over smaller. In fact, size-selective vertebrate predation may be one evolutionary factor that explains why insects as a group remain small in body size.

In contrast to the idea that small size aids insect defense, there has been little discussion of the possibility of large size serving an antipredator function in insects. For example, neither Edmunds (1974), Harvey & Greenwood (1978), Cloudsley-Thompson (1980), Hermann (1984), Endler (1986, 1991), Evans & Schmidt (1990), New (1991) nor Ruxton et al. (2004), discuss large size as an evolved antipredator mechanism in insects. However, we believe that under certain circumstances, large body size can greatly enhance insect survival against both invertebrate and vertebrate predators, and therefore may be under positive directional selection.

In this paper, we argue that large size serves as an antipredator defense in two species of lubber grasshopper (Romalea microptera (Beauvois) and Taeniopoda eques (Burmeister), family Romaleidae)1. We provide evidence to support five points: 1) Vertebrate predation typically selects against large size in insects. 2) Lubber grasshoppers are chemically and behaviorally defended against most vertebrate predators. 3) Escape from vertebrate predation has released lubbers from predatory small-size selection, allowing them to evolve a larger size. 4) Large size is highly beneficial to lubber grasshoppers vis-à-vis both invertebrate and vertebrate predators, and as such, is evolutionarily favored as an adaptive antipredator trait. 5) This syndrome is common among chemically defended grasshoppers, which tend to be larger than palatable grasshoppers.

Results and Discussion

1) Vertebrate predation selects against large size in insects.—Insect predator-prey interactions are extremely diverse and complicated (Evans & Schmidt 1990, New 1991, Woodward et al. 2005), and nearly all types of interactions are possible. However in general, larger arthropod prey are more conspicuous to vertebrate predators than are smaller arthropod prey (Curio 1976, Winfield & Townsend 1983, Schülert & Dicke 2002, Shine & Thomas 2005). This is partly because the probability of encountering/detecting a prey item increases as prey size increases (Maly 1970, Ware 1972, Curio 1976, Maiorana 1981, Bell 1990, Goerlitz & Siemers 2007, Troost et al.). In addition, small insects can more easily hide behind small objects or enter small cavities inaccessible to large predators, such as under bark or rocks, or between tight-fitting plant parts (Edmunds 1974). Although maximum running and flying speeds in insects scale positively with body size (Dudley 2000, 2002; Bonner 2006), flying insects usually escape flying predators not by speed, but by maneuverability (Cloudsley-Thompson 1980) and acceleration, both of which are inversely proportional to body size (Dudley 2000, 2002) (e.g., syrphid flies vs large beetles, dobsonflies, mantids, etc.: McLachlan et al. 2003). Likewise, small insect species typically exhibit greater burst-acceleration during escape-jumping than large species (e.g., fleas, flea beetles, and leaf hoppers vs crickets) (see Alexander 1985), and smaller individuals are theoretically more maneuverable than larger ones when running (Full et al. 2002). These size-relationships imply that larger insects may be under greater threat than small insects from vertebrate predators.

Both optimal foraging theory (Stephens & Krebs 1986) and empirical evidence (Prop 1960, Tinbergen 1960, Mattson et al. 1968, Curio 1976, Churchfield et al. 1991, Schülert & Dicke 2002), suggest that when all other things are equal, vertebrate predators prefer larger over smaller insect prey items, because large insect prey are energetically more nutritious and are often easier to capture (O’Brien et al. 1976, Morin 1984, Chen et al. 2004, McCracken et al. 2004; but see Shine & Thomas 2005). For example, broad-headed skinks, Eumeces laticeps, selected large crickets and ignored small crickets when offered both simultaneously (Cooper et al. 2007), and all of six species of insectivorous mammals tested by Dickman (1988) preferred large vs small cockroaches. Field studies show that large insects are more susceptible to vertebrate predation than small insects (Exnerova et al. 2003). For example, larger insects comprised only 2% of “available” prey, but 28% of all prey items fed by water pipits, Anthus spinoletta, to nestlings (Brodmann & Reyer 1999). Likewise, sphingid caterpillars represent 70% of the biomass fed by trogons, Trogon elegans, to their nestlings, and 98% of the sphingid prey were the last (largest) instar (Janzen 1993). Finally, many field studies show that birds, which in some communities consume enormous numbers of grasshoppers (Bryant 1912; Smith & Popov 1953; Greathead 1966; Joern 1986, 1992; Johnson et al. 1987; Fowler et al. 1991; Bock et al. 1992; Ji et al. 2008), prefer large, over small grasshoppers (Stower & Greathead 1969, Belovsky 1990, Belovsky et al. 1990, Belovsky & Slade 1993, Gardner & Thompson 1998).

On a community scale, each vertebrate predator species restricts itself to a specific range of prey sizes (Sinclair et al. 2003, Radloff & Du Toit 2004, Churchfield & Rychlik 2006, Montoya & Burns 2007, Whiting et al. 2007, Owen-Smith & Mills 2008). This range very often exceeds the largest, but not the smallest insect size – i.e., many vertebrate predators can take prey several orders of magnitude larger than the largest insects, but cannot successfully prey on the smallest insects (Wilson 1975, Sinclair et al. 2003). This is seen with large alligators (pers. obs.), owls (Craighead & Craighead 1956, Salvati et al. 2001), hawks (Craighead & Craighead 1956, Johnson et al. 1987), storks (Smith & Popov 1953, Falk et al. 2006), fox (Aranda 1995), coyotes (Fichter et al. 1955, Ortega 1987), hyenas (Kingdom 1997), bears (Chapman & Feldhamer 1982) and African leopards (Ray & Sunquist 2001), all of which take both insects and much larger vertebrate prey.

In contrast, some very large insects can escape predation by the smallest vertebrates (salamanders, tiny frogs, small birds); however, many small vertebrates can handle large insect prey by ingesting them in pieces (birds, mice, some lizards) (Kaspari 1990) or by having exceptionally large mouths or expandable gullets (Emerson et al. 1994). In addition, even if an insect species did gain protection against small vertebrates by evolving a larger size, that would presumably make that insect prey even more conspicuous and attractive to the numerous larger vertebrate predators in that same community (e.g., Pearson 1985). As such, insects generally cannot escape vertebrate predation by evolving a larger body size.

In contrast, insects can escape vertebrate predation by evolving smaller size. Arthropod size decreases by an order of magnitude below the small-size limit for acceptance by most vertebrate predators (except small fish and larval amphibians). Indeed, mites, Collembola, thrips, Psocoptera, Zoraptera, aphids, whiteflies, lice, fleas, and many scale insects, beetles, Diptera, Hymenoptera, and early instars of many insects are simply below the acceptable prey-size range of most vertebrate predators. Hence, vertebrates are a strong selective force against large insect size, but not against small insect body size (Nylin & Gotthard 1998).

2) Lubber grasshoppers are chemically and behaviorally defended against most vertebrate predators.— The lubber grasshoppers Romalea microptera and Taeniopoda eques are closely-related species from North America. R. microptera inhabits the southeastern portion of the USA, whereas T. eques survives primarily in the Chihuahuan Desert of the southwestern USA and northern Mexico (Rehn & Grant 1959, 1961). Their morphologies, behaviors and antipredator defenses are similar to each other, and different from all other North American grasshoppers (Stuaffer & Whitman 2007). These two species are so closely-related that they can interbreed and produce fertile offspring in the laboratory (Whitman unpub.). Because of their close relatedness and similarity in defense traits, we will combine the results from both species, in this paper.

These two grasshopper species are chemically defended by two, nearly identical, two-component antipredator mechanisms. The first mechanism is a secretory defense derived from the respiratory system, and unique among arthropods. In both species, the spiracular tracheal trunks of the metathorax produce and store an odorous, noxious secretion that is sprayed out at attacking predators. This defensive secretion emerges from the metathoracic spiracles first as a dispersive spray, and then as an adherent froth (Fig. 1) (Whitman et al. 1991, 1992). It contains a witches' brew of low-weight phenolics, quinones, aldehydes, ketones, alcohols, organic acids, terpenoids, and miscellaneous other substances (Jones et al. 1988, Polanowski et al. 1997).

Fig. 1.

R. microptera grasshopper expelling odorous, frothy defensive secretion from metathoracic spiracles. See Plate VI.

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Some of the secretion components are synthesized by the insect itself, whereas others are derived from its diet. Lubbers are poison-plant generalists, and they sequester many plant toxins into their tracheal defense glands. For example, lubbers that feed on onion or garlic secrete a variety of plant-derived sulfur compounds characteristic of those plants (Jones et al. 1987, 1988, 1989). Lubbers that feed on catnip sequester and secrete terpenoid lactones (Blum et al. 1990), and those that feed on diets high in catechol or hydroquinone, sequester and release large amounts of these substances (Snook et al. 1993). As such, this unique defense gland serves as a toxic waste dump for potentially harmful, plant secondary compounds. When ejected, these low-weight substances quickly volatize, enveloping the grasshopper in a noxious chemical cloud, deterrent to many vertebrate predators (Fig. 2). We have observed naïve lizards and birds violently fling lubbers from their mouths after secretion ejection. Some predators gagged or wiped their mouths or snouts on the substrate after encountering this pungent and irritating exudate (Fig. 3) (Whitman et al. 1985, Yosef & Whitman 1992).

Fig. 2.

T. eques defensive display in response to inquisitive mouse. Display includes visual (aposematic colors, twisting abdominal tip and antennae, elevated wings, jumping and thrusting hind legs), acoustic (auditory discharge of defensive secretion and sometimes wing stridulation), mechanical (spiny hind legs and biting), and chemical (defensive secretion, regurgitation, defecation, and toxic blood) elements. Note defensive secretion emerging from metathoracic spiracles. See Plate VII.

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Fig. 3.

Grasshopper mouse Onychomyes torridus, rubbing face and paws in dirt, after becoming contaminated with blood and defensive secretion of T. eques grasshopper. See Plate VII.

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The second mechanism of the chemical defense system of lubbers is an internal toxin, apparently synthesized by, and present in, all lubber instars (Whitman 1990). It is relatively potent, and consumption of a single 2nd instar lubber can induce vomiting in an inexperienced bird or lizard (Fig. 4). Often a naïve vertebrate predator will attack the first few lubbers it encounters, then after experiencing the negative effects (Figs 3–5), will refuse to attack subsequent offerings. Such food-aversion conditioning is probably highly adaptive to predators, because consumption of lubbers can be lethal (Whitman unpub.). The internal toxin has not been chemically identified, but is present even in first-instar nymphs fed lettuce (Whitman & Orsak 1985).

Fig. 4.

Anolis carolinensis lizard that has just vomited after swallowing a toxic R. microptera grasshopper nymph. This predator refused to attack subsequent lubbers. See Plate VIII.

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Fig. 5.

Left: A naive Didelphis marsupialis opossum eating a toxic R. microptera grasshopper. Right: Same opossum vomiting after consuming several R. microptera grasshoppers. This predator refused all subsequent lubbers offered. Photos by Larry Orsak. See Plate VIII.

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Dual-mechanism chemical defenses are common in insects, where a volatile secretion often serves both a rapid warning or alerting function for naïve predators, and a memory-eliciting function for experienced predators (Whitman et al. 1985, 1986, 1990, 1991). A second substance, held in the blood or body tissues, then poisons the predator, inducing food-aversion conditioning and a lasting learned association to the first defense (Whitman et al. 1990).

In lubbers, these two defenses have different effects on predators. The secretion alone can deter some invertebrate and vertebrate predators outright (Eisner et al. 1971, Jones et al. 1989, Blum et al. 1990), but seems to have less effect against others, such as preying mantids, wheel bugs, large spiders, centipedes, toads, and some mammals.2 By contrast, the internal defense is highly toxic to birds and lizards, partially toxic to toads and mammals, and only mildly deterrent to invertebrate predators (see below).

Strong chemical defenses explain why lubbers can afford to be flightless, lumbering, brightly colored, large, gregarious, and often extremely abundant in nature: we have recorded > 900 individuals per 100 m2 (Lamb et al. 1999). Despite their abundance, conspicuous appearance and sluggish nature, lubbers seem to suffer little vertebrate predation. Indeed, during 38 h of field observations of large and dense populations of active and conspicuous lubber grasshoppers inhabiting natural and old-field habitats, we recorded 102 individual insectivorous birds from 17 species foraging among the grasshoppers, and only observed one bird attack a lubber, despite observing constant bird attacks on other insect species (Whitman, unpubl.).3

Although some mammals (mice, rats, raccoons, opossums) and toads will occasionally consume a few lubbers, these predators are generally not a threat because they hunt at night, and lubbers roost at the tops of vegetation from dusk to dawn (Whitman 1987). In summary, lubbers are generally immune to vertebrate predation, due to a combination of toxins and nocturnal roosting.

3) Escape from vertebrate predation releases lubbers from small-size selection, allowing them to evolve large size.— Most organismal traits are thought to be under conflicting selection pressures (Mayr 1956, Slatkin 1984, Schluter et al. 1991, Mayhew 2006). This is certainly the case for body size (Roff 1981, 2002; Nylin & Gotthard 1998; Blanckenhorn 2005; Lomolino 2005; Mänd et al. 2007), where any number of factors could select for large size (e.g., fecundity, sexual selection, surface-volume relationships, desiccation resistance, thermal inertia, lowered mass-specific metabolic rates, increased strength, ability to consume tough food, locomotion, and increased food and water reserves, etc.) (Peters 1983, Schmidt-Nielsen 1984, Honěk 1993, Roff 2002, Chown & Nicolson 2004, Makarieva et al. 2005, Vincent 2006, Vincent & Herrel 2007, Whitman 2008). Likewise, any number of factors might select for small size, the most important being viability selection from either time constraints or predative pressures (Stearns 1992, Blanckenhorn 2000, Roff 2002). As previously discussed, vertebrate predation may select for small size in insect prey, and this may be a contributing reason to why most grasshoppers and most insects are relatively small in comparison to vertebrates.

Hence, for most species, there are probably manifold environmental factors selecting for both large and small body size, during each generation; and for many populations, body-size evolution may have already reached relative equilibrium under a balance of conflicting selective pressures (Thompson & Fincke 2002). However, when specific selective factors change in strength, we would expect natural selection to alter mean population trait values, given additive genetic variance and heritability in these traits. We suggest that this occurred in lubber grasshoppers.

We hypothesize that the ancestors of lubber grasshoppers began feeding on vertebrate-toxic plants, which imbued them with chemical defenses against many vertebrates. We further hypothesize that escape from vertebrate predation, due to the continued evolution of ever more potent chemical defenses, altered the balance of size-selective forces, allowing lubbers to reach a new equilibrium for body size. The reduction of a powerful selective force (vertebrate predation) destabilized the previous balance between competing selective forces, allowing lubber body size to increase over evolutionary time until directional selection for small size (Blanckenhorn 2000, Thompson & Fincke 2002) once again approximated that for large size.

A similar ecological release from predation is thought to be a major factor favoring island gigantism in a wide range of taxa (Foster 1964, Case 1978, Smith 1992, Lomolino 2005, but see Meiri et al. 2006, Raia & Meiri 2006), including many island insects (Brindle 1970, Gibbs 1998, Priddel et al. 2003, Evenhuis & Eldredge 2004, Bell et al. 2007). Population decline or extinction of these island giants, following introduction of new predators to their habitats, support the hypotheses that, for invertebrate prey, large size is at a distinct disadvantage against vertebrate predators, and that lack of predators can favor the evolution of large size (Brindle 1970, Gibbs 1998, Priddel et al. 2003, Jones et al. 2005). Similar decreases in large zooplankters are seen when vertebrate predators (fish) are introduced to ponds (Roff 2002), reconfirming that vertebrate predators are generally a selective force for small size in invertebrate prey.

Did acquisition of chemical defense in lubbers allow the evolution of large size? R. microptera and T. eques are perhaps the most poisonous grasshoppers in the USA (Whitman 1990), and are also the largest (Rehn & Grant 1959, 1961; Whitman 1988). Although correlation does not prove cause, our data (below) provide experimental evidence to support our hypothesis linking large size with escape from vertebrate predators, as a consequence of chemical defense.

4) Large body size is a highly beneficial antipredator trait in lubber grasshoppers.—Each invertebrate predator species generally attacks prey within a certain size range (Holling et al. 1976, Pearson & Mury 1979, Scarborough 1978, Dennis & Lavigne 1985, Warren & Lawton 1987, New 1991, Dixon & Hemptinne 2001, Olberg et al. 2005, Okuyama 2007, Sloggett 2008). For example, hunting spiders and other invertebrate predators favor small over large grasshopper prey (Belovsky et al 1990, Ovadia & Schmitz 2002). This is partially because capture efficiency declines and danger to the predator increases, as prey size and strength increase beyond the optimal prey-size range (Dixon 1959, Morris 1963, Stortenbeker 1967, Dixon & Russell 1972, Wilson 1975, Griffiths 1980, Vermeij 1982, Bailey 1986, Iwasaki 1991, New 1991, Reavy 1993, Cogni et al. 2002, Okuyama 2007).

Except in certain cases (such as in social or trapping predators – e.g., Enders 1975, Hölldobler & Wilson 1990, Kim et al. 2005, Souza et al. 2007), the vast majority of predaceous arthropods will not, or cannot, successfully attack prey much larger than themselves (Shelly & Pearson 1980, Nentwig & Wissel 1986, Wheater 1988, Sabelis 1992, Cohen et al. 1993, Montllor & Bernays 1993, Matlock 2005, Olberg et al. 2005). As Warren & Lawton (1978) suggest, “Invertebrate predators usually eat prey of about their own size or smaller . . .”. Those that occasionally attempt to capture large prey usually fail (Dixon & Russell 1972, New 1991), such as when ants attack large vertebrates, which simply move away. One might expect predaceous arthropods to evolve larger sizes to make use of large prey; however, arthropod predators are under the same vertebrate predator-enforced small-size selection as other arthropods.

The inability of predacious arthropods to take large prey is a weakness that can be exploited by any invertebrate prey species that can evolve large body size. Insects are normally constrained from evolving large size, in part by increased liability to vertebrate predators. However, insect prey with effective antivertebrate predator defenses are released from this constraint, allowing them to evolve larger body size, which then reduces invertebrate predation.

We tested the hypothesis that large size is an advantageous antipredator trait in lubber grasshoppers. A full accounting of these experiments will be presented elsewhere, but we will provide a brief description of the methods and results here. We tested wild ants and birds in the field. For spiders, preying mantids, wheel bugs, and frogs, we used naive predators collected from the wild, and then acclimated to laboratory conditions for several days. Trials began only after the predator routinely attacked and ate edible prey (Acheta domestica crickets, Tenebrio molitor mealworms, Galleria mellonella wax-moth caterpillars, Musca domestica house flies, etc.) that were offered. In each laboratory trial, a single predator individual was allowed to acclimate to a single cage or arena. We then gently introduced a single R. microptera grasshopper of a specific size, and recorded if the grasshopper was or was not attacked. Table 1 shows size and mass for various R. microptera instars.

Table 1.

Approximate body lengths (frons to abdomen tip) and mass of various R. microptera instars. Note that both length and mass increase within each individual stadium.

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We collected 42 wolf spiders, Hogna carolinensis (Lycosidae), by headlamps at night near Tifton, Georgia, and divided them into six treatment groups, each balanced for body mass, which ranged from 0.30 to 1.72 g. Spiders were maintained in individual 1-L plastic containers and given an adult cricket on the day of capture, and water thereafter. Four days later, we introduced a single R. microptera grasshopper into the container and recorded if the spider did or did not attack the grasshopper during the next 15 min. Here, attack is defined as lunging at and covering prey with the fore-legs and anterior body. Each spider was tested once. Table 2 shows that the spiders refused to attack large, late-instar grasshoppers. In fact, spiders often fled from 5th -instar and adult grasshoppers.

Table 2.

Attack rate of Honga carolinensis wolf spiders on R. microptera grasshoppers of different sizes and instars. Seven different spiders tested for each grasshopper size class; each spider tested once.

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We collected adult Chinese preying mantids, Tenodera aridifolia near Normal, Illinois. Mantids were maintained in 4-L containers and fed various insects until testing began. Each of the 21 mantids was tested with seven size classes of R. microptera over the course of 13 d. Mantids were offered grasshoppers on odd days and allowed to consume crickets, mealworms, wax-moth larvae or house flies on even days. Each test consisted of introducing a R. microptera of one of seven sizes (see Table 3) into the mantid's container for 1 h. Each mantid received a different sequence of grasshopper size classes. Mantids were not allowed to consume captured lubbers.

Table 3.

Attack rate by adult male and female T. aridifolia preying mantids against various sizes and stages of R. microptera grasshoppers. Eleven female and ten male mantids were offered all size classes of grasshopper, individually on different days. Mantids attacked significantly more of the small grasshopper-size classes than the large size classes, and larger mantids attacked larger lubbers (Spearman's rho = 0.675, df = 21, p < 0.001; Fig. 6).

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The results show that the mantids attacked significantly more of the small grasshopper size classes than the large size classes (Table 3), and that larger mantids attacked larger lubbers (Spearman's rho = 0.675, df = 21, p < 0.001; Fig. 6) . Male and female mantids differed in the mean size of prey taken. Female mantids are larger (mean ± SD: mass = 2.14 ± 0.35 g; body length = 8.95 ± 0.56 cm, n=11) than males (mass = 1.38 ± 0.19 g; body length 7.95 ± 0.32 cm, n=10), and attacked larger prey than males (Mann Whitney U = 26.5, df = 20, p < 0.05). Male mantids refused to attack adult lubbers, whereas female mantids attacked four lubber adults (Table 3). Some mantids exhibited threat or defensive behavior, but only against large grasshoppers.

Fig. 6.

Adult mantid (Tenodera aridifolia) body mass vs largest lubber size class (instars 1 to 5 or adult male or adult female) attacked. Mantids attacked significantly more of the small grasshopper size classes than the large-size classes, and larger mantids attacked larger lubbers (Spearman's rho = 0.675, df = 21, p < 0.001). Open circles indicate male mantids and closed circles indicate female mantids. See Table 3.

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Two male mantids backed away from 5th instar lubbers, four backed away or performed defense/threat displays to adult male lubbers, and four to adult female lubbers. In two cases, male mantids attempted to fly away from approaching adult grasshoppers. Female mantids displayed defense/threat against one 5th instar, four adult males, and three adult female lubbers. Table 3 shows attacks; however, not all attacks were successful and larger-sized lubbers tended to escape mantid attacks more often. One male mantid dropped a captured 4th instar after the grasshopper raked its hind tibial spines across the face of the mantid. The same result occurred with an adult female mantid and an adult male lubber. Interestingly, only two of the four attacks by female mantids on adult lubbers resulted in capture; in two cases, the female's raptorial legs bounced off of the hard cuticle of the grasshopper's prothoacic shield. In other unpublished tests, we have observed large captured lubbers struggle wildly, pulling, pushing, twisting, or kicking themselves free of a mantid grasp. In such cases, the mantid did not re-attack.

We tested 23 adult wheel bugs, Arilus cristatus, against three lubber size classes. Bugs (mean ± SD body length and mass, female : 3.1 ± 0.14 cm, 0.83 ± 0.16 g; male: 2.7 ± 0.10 cm, 0.36 ± 0.033 g) were captured in McLean Co., Illinois, and thereafter maintained in clear 500-ml ventilated plastic containers and fed a variety of palatable insects. Each bug was tested against three different R. microptera instars: 1st, 3rd, and 5th at three- to six-day intervals in a balanced presentation sequence. Bugs were fed a cricket or wax moth larvae then starved for 3 to 5 d, then tested. Each test consisted of placing one lubber in the bug's container for 24 h. After the test, the bugs were fed a palatable insect and starved again for 3 to 6 d prior to the next round of testing. After each 24-h test, we recorded which bugs had eaten lubbers. Previous unpublished tests had demonstrated that this species does not develop food-aversion conditioning toward lubber grasshoppers. The results (Table 4) show that the bugs fed only on smaller-sized grasshoppers (χ2 = 19.7, df = 2, p < 0.001). None of the 23 bugs consumed a 5th instar lubber, whereas 18 consumed a 1st instar lubber. During our observations, no bugs performed threat or defensive displays (elevating fore body, front legs and head, rearing back, walking backwards or flying away from an approaching grasshopper) to 1st instar lubbers, but eight bugs did to the approach of 5th instar lubbers.

Table 4.

Predation by 23 adult Arilus cristatus wheel bugs (Reduviidae) on R. microptera grasshoppers. Each bug was offered a 1st, 3rd, and a 5th -instar grasshopper, at 3 to 6-d intervals, in a balanced presentation. Bugs consumed significantly more of the smaller sized grasshoppers (1st and 3rd instars) than the larger, 5th instars (χ2 = 19.7, df = 2, p < 0.001).

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We tested red imported fire ants, Solenopsis invicta (= wagneri), during a succession of sunny days in a pasture near Tifton, Georgia. Prior to the tests, we clipped (to within ~ 2 cm height) any weedy vegetation within 50 cm of the centers of the elevated, dome-shaped mounds, in order to remove visual obstructions. We started each test by scraping off the top of a fire-ant mound, exposing a flat area of ~ 14 cm diameter. After ~ 10 s, when hundreds of ants had moved to the exposed top of the mound, we then dropped three R. microptera individuals of different instars onto the center of the nest. This was repeated at different mounds until 10 grasshoppers of each of six size classes (five instars and adult males) were tested. We recorded as “escape” those grasshoppers that were able to move at least 50 cm from the center of the hive, whether or not they still had ants on their bodies. Grasshoppers unable to move 50 cm were recorded as “dead.” The results (Table 5) show that larger lubbers escaped more often from predaceous ants.

Table 5.

Ability of R. microptera grasshoppers of different sizes to escape from disturbed fire ant (Solenopsis invicta) mounds. Ten grasshoppers tested for each instar.

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We tested 22 northern leopard frogs, Rana pipiens, obtained from a biological supply company, against various R. microptera instars and sizes. Frogs were maintained in individual 4-L plastic jars with water, during which they were fed crickets, then starved for two days prior to testing. Trials ran for 10 d. Each frog was offered a single R. microptera grasshopper on odd days and an adult cricket on even days. Each frog received a different size-sequence of grasshoppers, such that the presentation sequence of lubbers of various sizes was balanced. Previous work suggests that frogs do not readily develop food-aversion conditioning to lubbers (Hatle & Faragher 1998), and indeed, attack rates did not decline between the 1st and the last days of testing. The results (Table 6) show that, against frog predators, large lubbers enjoyed a significant survival advantage over small lubbers. Over half of the 22 frogs attacked 1st instar lubbers, but no frogs attacked adult lubbers and only two frogs attacked 5st instar lubbers.

Table 6.

Predation rate by northern leopard frogs, Rana pipiens on various sizes and stages of R. microptera grasshoppers. Twenty-two frogs tested individually, each against five grasshopper size classes, with each grasshopper offered individually, on alternative days, in a balanced sequence.

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We tested wild, naive starlings, Sturnus vulgaris, and house sparrows, Passer domesticus against R. microptera grasshoppers in Normal, Illinois. We first trained these birds to feed at a feeder on frozen-then-thawed crickets, wax-moth larvae and mealworms, and 0.5-g pieces of moist cat food. After two or three days, when the birds repeatedly and aggressively fed at the feeder, we placed out three feeders, each separated by ~ 60 cm. One feeder contained one each of a living 1st, 2nd and 3rd-instar R. microptera, tied to the feeder by thin strings. The 2nd feeder contained a live 4th and a live 5th-instar grasshopper, and the 3rd feeder contained a live-tethered adult male and adult female grasshopper. We separated the lubber size classes onto different feeders because trials a year earlier showed that the birds were hesitant to approach the feeders containing adult grasshoppers. Wariness in birds increases with prey size (Gamberale & Tullberg 1998). The feeders were placed out at dawn and inspected and removed as soon as feeding had occurred (13 min to 2.2 h). Overall, we tested at four locations, each at least 1.2 km from the others. We assume that each test involved a different flock of birds. We tested at each site only once. In some cases we do not know which species of bird ate or attacked lubbers, and so we have combined the response for the two bird species.

Table 7 gives the number of grasshoppers attacked (defined as wounded, missing body parts, gone from the feeder, or observed to be taken by a bird). The results show that large lubbers were not attacked. Indeed, not a single 5th instar, adult male, or adult female R. microptera was damaged. In contrast, nearly all small individuals were damaged, killed, or missing from the feeders during each of the four tests. These wild birds had probably never encountered these grasshoppers, because lubbers do not exist in the midwest of the USA. These, presumably naive, birds sampled lubbers, even though this prey is warningly colored and chemically defended.

Table 7.

Predation rate on various-sized R. microptera by wild, naive starlings and house sparrows at feeders. Four of each prey size offered. See text for additional methods.

i1082-6467-17-2-353-t07.gif

In all of our experiments, testing seven different predator species from different taxa (spider, preying mantid, wheel bug, ant, frog, starling and sparrow), large lubber instars enjoyed a highly significant advantage against predation: predators tended to attack or overcome smaller size classes of lubber grasshoppers, but refused to attack or failed to overcome large-sized lubbers. These data demonstrate a strong advantage for large body size for lubber grasshoppers against predators. Most surprising is that larger lubber body size decreased both invertebrate and vertebrate predation. As such, our results suggest that large size in an insect can be an antipredator defense, against both vertebrate and invertebrate predators (Fig. 7).

Fig. 7.

Adult R. microptera grasshoppers are simply too large for some small vertebrate predators to attack. See cover.

i1082-6467-17-2-353-f07.jpg

5) Chemically defended grasshoppers are generally larger than their non-chemically defended relatives.—We wanted to know if large body size was associated with chemical defense in other grasshopper species, and therefore we compared body sizes of chemically defended grasshoppers to those of grasshopper species that lack chemical defenses. We obtained body-size data for female grasshoppers from various faunal monographs and field guides, and present the data here as geographic or taxonomic summaries (Figs 8–10, Table 8). We also list all the grasshopper species known or suspected by us to be chemically defended (see Whitman 1990), and provide size and mass data when available (Table 9).4

Fig. 8.

Body length distributions for grasshopper species (females only) from various geographic areas. See Table 8 for sources of data. “Southern Africa & Madagascar” includes Congo, Angola, and Madagascar.

i1082-6467-17-2-353-f08.gif

Fig. 9.

Top: body-length distributions for grasshopper species (females only) for African and Thai Pyrgomorphidae, including from North Africa (Chopard 1943), Congo (Dirsh 1970), Angola (Dirsh 1966), Madagascar (Dirsh 1963), and Thailand (Roffey 1979). Bottom: female body-length distribution for USA Melanoplinae from Capinera et al. 2004. In each case, known chemically defended species are designated in grey, and nonchemically defended species in white.

i1082-6467-17-2-353-f09.gif

Fig. 10.

Body-mass distribution for 31 species of grasshopper from the western USA. Top: males. Bottom: females. Nearly all are <1g. Data from Pfadt 1994.

i1082-6467-17-2-353-f10.gif

Table 8.

Percentage of grasshopper species with females under 4-cm body length for different geographic regions.

i1082-6467-17-2-353-t08.gif

Table 9.

Body sizes of chemically defended grasshoppers. Note that females of most species >2g and 4 cm. * no sex specified.

i1082-6467-17-2-353-t09.gif

Among the ~13,000 species of grasshopper (Orthoptera Species File), adult body mass ranges across three orders of magnitude, length by 1.5 orders of magnitude: from ~ 15 mg and 5 mm for tiny adult male Illapelia penai from South America (Carbonell & Mesa 1972), to 30,000 mg and ~ 120 mm (head to tip of abdomen, and 145 mm (to wing tip) for the largest female individuals of Tropidacris cristata from Central and South America (Uvarov 1966, Rowell 1983, Carbonell 1986). In general, grasshopper mass, shape, and length vary with family, latitude, and life form, with the largest species usually inhabiting warmer climates (Uvarov 1966, 1977). Ground-dwelling, “terricolis” grasshoppers tend to be robust and heavy, and grass-mimicking species (e.g., Acrida, Achurum) tend to be long, thin and light.

However, even with such wide background variability in size, shape, and mass among grasshoppers, there are striking trends related to chemical defense. First is that the majority of females of all grasshopper species are under 1 g and 4 cm (Table 8, Figs 8–10). By comparison, the females of most of the ~ 40 known chemically defended species of grasshopper (from among seven subfamilies) are heavier than 2 g and longer than 4 cm (Fig. 9, Table 9). Figure 9 gives female body sizes for some pyrgomorphids from Africa and Thailand, and also for USA Melanoplinae; chemically defended species are designated in grey. Note that in each case, the chemically defended species sort to the larger-sized classes. Thus, chemically defended grasshoppers tend to be larger than nonchemically defended grasshoppers.

A problem in our analysis is that many palatable grass-mimicking grasshoppers are very long, thus weakening the correlation between chemical defense and body length. However, such grasshoppers weigh substantially less than chemically defended grasshoppers, which tend to be robust and heavy. Mass is a better metric than length for predicting ecological interactions, in part because mass scales as the cube of length for isometric bodies (Peters 1983, Calder 1996). Hence, a doubling of body length would increase volume and mass by eight times, for individuals with the same relative dimensions. Although chemically defended grasshoppers may be only somewhat larger than palatable grasshoppers, they are substantially heavier. Unfortunately, grasshopper fresh-body masses are difficult to come by. However, Pfadt (1994) gives fresh adult mass for 30 common Western USA species (Fig. 10). Of these, the greatest mean female mass was 1.65 g, and females of only three species exceeded 1.0 g. In comparison, median wet masses for females of chemically defended grasshoppers center around 4 to 5 g (Table 9).

Another problem is our incomplete knowledge of chemical defenses among grasshoppers. Many chemically defended species are yet to be discovered, and in many cases we only have strong, not conclusive, evidence for chemical defense. For example, the largest grasshopper known, T. cristata (see above), is probably chemically defended, as they (and some other Romaleinae – including Tropidacris, Chromacris, and Taeniopoda; see Table 9) possess many of the traits characteristic of the chemical defense syndrome (Whitman et al. 1985): they feed on toxic plants, and the nymphs aggregate and flaunt bright (presumably warning) colors (Rowell 1983, Carbonell 1986, Whitman unpub.). Locust species, two of which have been found to be chemically defended when in the gregarious, swarming, phase (Sword 1999, Despland & Simpson 2005, Simpson & Sword 2009), also tend to be large and heavy (Uvarov 1966, 1977). Some larger-bodied locust species, Proscopiidae, Pyrgomorphidae, Pamphagidae and Romaleinae may likewise be chemically defended (Schultz 1981, López et al. 2007), but we will not know until careful predator-feeding trials are completed.

In summary, large size appears to be correlated with chemical defense in grasshoppers. And, as our results demonstrate, large size in an insect can deter invertebrate predation. This supports the hypotheses that large size is beneficial for chemically defended grasshoppers and that escape from vertebrate predation (via chemical defense) allows some grasshoppers to evolve large size.

General discussion

Copious evidence suggests that predation can be a strong selective force on prey morphology (Kittlewell 1973, Swain 1992, Heinrich 1993). Although large size is perhaps the most successful defence in vertebrates (e.g., elephants and rhinos), large body size has seldom been considered as an antipredator defense in insects. However, our results show that large lubber size is highly beneficial against both invertebrate and vertebrate predators, and thus serves as a defensive trait.

In our trials, the largest lubber grasshoppers were relatively immune to predation. Note that we selected as test predators, the largest wolf spider (Honga carolinensis), largest mantid (Tenodera aridifolia), and the largest reduviid species (Arilus cristatus) in the USA, as well as a very aggressive ant species (Solenopsis invicta). Presumably, lubbers would enjoy even greater protection against the more common smaller and less aggressive invertebrate predators that share their habitats. In addition to size-escape from invertebrate predation, our results show that large lubber size can deter vertebrate predators as well (Tables 6, 7). As such, lubbers have come to occupy a relatively predator-free niche.

We suggest that large size in lubber grasshoppers evolved as a direct consequence of chemical defense against vertebrate predators. We further propose that large size is a common antipredator trait among chemically defended insects. Chemically defended insects often possess a suite of characteristics that are diametrically opposite to those of nonchemically defended insects (Salazar & Whitman 2001). This ensemble of traits has been named the Chemical Defense Syndrome (CDS), and includes chemical defense, visual, chemical, and/or mechanical (tactile or auditory) warning signals (aposematism) and threat displays, aggregation, exposed diurnal behavior, flightlessness, sluggishness, and large size (Whitman et al. 1985, Yosef & Whitman 1992, Salazar & Whitman 2001). Not all chemically defended insects exhibit all of these traits, but enough do to validate the principle.

Various components of the CDS have been thoroughly examined (Ruxton et al., 2004), such as chemical defense (Blum 1981, Whitman et al. 1990, Eisner et al. 2005), aposematism (Guilford 1990, Prudic et al. 2007), aggregation (Vulinec 1990, Costa 2006), and sluggishness (Hatle & Whitman 2001, Hatle et al. 2002). However, large size as a component of the CDS has received little attention, despite its apparent common association with chemical defense across numerous insect orders (Pasteeles et al. 1983), and the fact that the efficacy of warning coloration increases with body size (Nilsson & Forsman 2003).

The consequences of this association are not trivial: the presence or absence of chemical defense may be an important factor in body size evolution in insect prey (Forsman & Merilaita 1999). In fact, just the presumption of chemical defense may be enough to influence body-size evolution, such as in those Batesian mimics that lack chemical defenses, but mimic large insects that do. An example may be seen in the barklice (Psocoptera), nearly all of which are cryptic and ≤ 5 mm long (Mockford 1993), except for a group of giant-bodied (up to 11.5-mm long) Psocoptera from Central America that apparently mimic assassin bugs and wasps (Mockford 1992). Whether these giant barklice are actually chemically defended or are only mimics is unknown. However, the important ecological and evolutionary reality is that they appear to be defended, and as a result presumably suffer less predation and less selection for small size.

Another feature of many species of chemically defended grasshoppers is that (like lubbers), their chemical defenses often work better against vertebrate predators than invertebrate predators (Whitman 1990). For example, both birds (Descamps & Wintrebert 1966) and humans (Steyn 1962) have died after eating toxic Phymateus grasshoppers. Euw and coworkers (1967) calculated that a single Poekilocerus bufonius contained enough cardenolide to kill a cat. Greg Sword experienced golf-ball sized lymph nodes after consuming a single Schistocerca emarginata grasshopper (Sword 2000), and we thank him for his personal commitment to understanding the dynamics of chemical defense in Orthoptera.

Of course, there is great variability among the interactions of the ~ 40 known chemically defended grasshopper species and their > 200,000 species of potential predators. However, for those protected species that have been thoroughly studied, there are usually several species of invertebrate predator that are not deterred by the chemical defenses of the grasshopper (Whitman 1990, Sword 2000). Insect chemical defenses may have evolved primarily against birds (Pasteels et al. 1983, Brower 1984, Rothschild 1985), and chemical defense in grasshoppers may have evolved primarily against vertebrate predation.

Our results suggest a broader evolutionary theme. The evolutionary path of a species is guided by phylogenetic and ecological constraints. Major evolutionary changes and rapid speciation and diversification follow those rare breakthroughs when a taxon eliminates a constraint. Body size, as all organismal traits, is under conflicting selection pressures, with some factors selecting for small and others for large size. A change in strength or direction in any one factor can alter the overall balance between these competing selective forces, pushing (or allowing) the population to evolve until a new equilibrium body size is reached. Such a process might explain some cases of island gigantism (Evenhuis & Eldredge 2004, Lomolino 2005, Bell et al. 2007), the loss of pigment and eyes in cave-dwelling species (Culver 1982), the loss of flight and defensive behavior in island-dwelling birds (MacArthur & Wilson 1967) and the correlation of defense mechanisms with predator sympatry, but not allopatry (Jones et al. 1978, Endler 1985).

In some cases, ecological or behavioral change stimulates a beneficial evolutionary breakthrough, which then alters overall selection dynamics, releasing a cascade of new evolutionary events. Such an “accidental” or serendipitous evolutionary breakthrough may lead to rapid increases in population density and range, speciation and radiation. Examples might include the evolution of lungs, flight, sociality, or chemical defense – all presumably beneficial traits that dramatically alter overall selection dynamics, leading to multiple changes in numerous other traits (e.g., Schmidt 1990). For example, chemical defense may be a prerequisite for the evolution of insect sociality (Starr 1985, Kukuk et al. 1989), or the many components of the CDS.

Perhaps the evolution of chemical defense in lubber grasshoppers was a breakthrough adaptation that sent them down a different evolutionary pathway, and set in motion a series of subsequent evolutionary events that profoundly altered their physiology, morphology, behavior, life-history, and ecology. This could have started when their cryptic and palatable ancestors encountered and fed on a vertebrate-toxic plant, which filled the insect's gut and oral and anal discharges with deterrent substances, causing reduced predation on that population (e.g., Jones et al. 1988, Sword 2001, Calcagno et al. 2004). Continued directional selection by predators could have then selected for specialization on toxin-providing food plants, and greater defensive capabilities (e.g., Jones et al. 1988, Dopman 2002), including all the traits of the Chemical Defense Syndrome (Whitman et al. 1985), such as aposematism, threat displays, gregariousness, flightlessness, sluggishness, and large size. Similar arguments have been made for other chemically defended groups (e.g., Schmidt 1990 for Hymenoptera).

Hence, the key evolutionary event for lubber grasshoppers may have been feeding on toxic plants, which increased defense against vertebrate predators, thus favoring the evolution of stronger chemical defenses. Escape from vertebrate predation (via toxins), released lubbers to evolve large body size, which then allowed them to escape from invertebrate predation via mechanical defense (large size). As such, the size difference between chemically defended lubber grasshoppers and their palatable relatives, represents the magnitude of the evolutionary force of vertebrate predation on grasshopper body size.

Of course large size has many benefits, including perhaps greater mating success, fecundity, homeostasis, an ability to consume tough food, dominate intraspecific competitors, and for grasshoppers, to lay egg pods deeper to thwart egg predators and parasitoids (Peters 1983, Andersson 1994, Calder 1996, Vincent 2006, Stauffer & Whitman 2007, Whitman 2008). Another reason large body size may be advantageous as an antipredator mechanism in insects is because it strongly covaries with the strength of mechanical defenses such as biting or kicking (Norman 1995, Burrows & Morris 2003, Vincent 2006, Vincent & Lailvaux 2008). Whereas small insects must rely on crypsis or rapid-escape behaviors to avoid predation (Dangles et al. 2007), larger species or instars can often generate strong forces during defensive kicking or biting behaviors. For example, another large bodied lubber grasshopper, Brachystola magna, can bite through human skin, and can employ its spiked hindlegs during defensive kicking bouts to generate upwards of 25 Newtons of force, enough to pierce the integument of some vertebrate and invertebrate predators (Vincent, pers. obs.). All of these factors should select for larger insect size. However, the fact that insects as a group remain small (Blanckenhorn 2000, Whitman 2008) suggests that the disadvantages of increasing size generally outweigh the advantages.

In this paper we propose that lubber grasshoppers evolved chemical defense prior to large size. However there are other scenarios for the evolution of size and defense in lubbers. Perhaps lubbers evolved large size first, which exposed them to increasing predation from vertebrates and placed them under strong selection to develop antivertebrate chemical defense. Hence, maybe chemical defense is a result of large size and not vice-versa.

Our results also confirm that predator threat changes with prey ontogeny, as in other insects (Dempster 1967, Stortenbeker 1967, Feeny et al. 1985, Dixon & Baker 1988, Belovsky et al. 1990, Medina & Barbosa 2002). For many insect prey, invertebrate predators attack the smallest instars or species, and vertebrate predators the larger instars or species (Watanabe 1976, 1981, Montllor & Bernays 1993). This is well documented in grasshoppers (Stower & Greathead 1969, Chapman & Page 1979, Belovsky et al 1990, Belovsky & Slade 1993), where smaller instars usually suffer higher rates of predative mortality than later (larger) instars (Stortenbeker 1967, Cherrill & Begon 1989, Danner & Joern 2003), and where predator species change with grasshopper growth (Stortenbeker 1967; Belovsky et al. 1990; Danner & Joern 2003, 2004). In lubbers, if the smaller, earlier instars suffer higher predation rates than the larger, later instars, then we might expect selection for large egg size and rapid growth (Paine 1976, Arendt 1997) of the small early stages. This may be the case for lubbers, which have one of the largest egg sizes known for grasshoppers (1 cm long and up to 43 mg fresh mass), and which are black as nymphs, which aids solar heating, growth, and development (Whitman 1987, 1988).

Lastly, we previously mentioned that predator-prey interactions are exceedingly complex. Because of such complexity, there are exceptions to nearly every generality that we have discussed. Hence, some small invertebrate prey are more conspicuous, more nutritious, and less agile than some large invertebrate prey species. Some vertebrates prefer smaller invertebrate prey, some invertebrate predators can capture large prey (Lorenz 2007), some chemically defended prey are quite small (Pasteeles et al. 1983), and some palatable insect prey are large. Furthermore, previous authors have anecdotally noted the defensive benefits of large body size in invertebrates, such as shellfish (Roff 2002), or documented the association between chemical defense and large size in insects (Pasteeles et al. 1983). However, we believe that overall, the generalities and principles proposed here are valid.

Acknowledgments

We thank Shin-Ichi Akimoto, Robert Alexander, Corey Bazelet, Murray Blum, Clive Jones, Robert Dudley, David Eades, Jahir Hussain, Shajahan Johny, Michel Lecoq, Daniel Otte, My Hanh Luong-Skovmand, Michael Samways, Melissa Stauffer, Tim Stauffer, Yoshikazu Sugano, and Gregory Sword for providing data, advice, or assistance.

References

1.

R. Mc N. Alexander 1985. The maximum forces exerted by animals. Journal of Experimental Biology 115:231–238. Google Scholar

2.

M. Andersson 1994. Sexual Selection. Princeton University Press. Princeton, NJ. Google Scholar

3.

Y. Aranda, J. Isern-Vallverdú, and C. Pedrocchi . 1995. Dieta estival del zorro Vulpes vulpes L. en pastos del Pirineo aragonés: relación con la abundancia de artrópodos. Lucas Mallada Revista de Ciencias 7:9–20. Google Scholar

4.

J. D. Arendt 1997. Adaptive intrinsic growth rates: an integration across taxa. Quarterly Review of Biology 72:149–177. Google Scholar

5.

P. C. E. Bailey 1986. The feeding behavior of a sit-and-wait predator, Ranatra dispar (Heteroptera: Nepidae): the combined effect of food deprivation and prey size on the behavioural components of prey capture. Ethology 71:315–332. Google Scholar

6.

P. W. Bateman and P. A. Fleming . 2008. An intra- and interspecific study of body size and autotomy as a defense in Orthoptera. Journal of Orthoptera Research 17:315–320. Google Scholar

7.

G. Y. Bei-Bienko and L. L. Mishchenko . 1963. Locust and Grasshoppers of the U.S.S.R. and adjacent Countries. I. Israel Program for Scientific Translations. Jerusalem. Google Scholar

8.

G. Y. Bei-Bienko and L. L. Mishchenko . 1964. Locust and Grasshoppers of the U.S.S.R. and adjacent Countries. II. Israel Program for Scientific Translations. Jerusalem. Google Scholar

9.

W. J. Bell 1990. Searching Behavior – the Behavioural Ecology of Finding Resources. Chapman & Hall. London. Google Scholar

10.

W. J. Bell, L. M. Roth, and C. A. Napela . 2007. Cockroaches: Ecology, Behavior and Natural History. John Hopkins University Press. Baltimore. Google Scholar

11.

G. E. Belovsky 1990. How important are nutrient constraints in optimal foraging models or are spatial/temporal factors more important. pp 255–280. In R. N. Hughes , editor. (Ed.). Behavioural Mechanisms of Food Selection. NATO ASI Series. Springer. Berlin. Google Scholar

12.

G. E. Belovsky and J. B. Slade . 1993. The role of vertebrate and invertebrate predators in a grasshopper community. Oikos 68:193–201. Google Scholar

13.

G. E. Belovsky, J. B. Slade, and B. A. Stockhoff . 1990. Susceptibility to predation for different grasshoppers: an experimental study. Ecology 71:624–634. Google Scholar

14.

R. S. Bigelow 1967. The Grasshoppers (Acrididae) of New Zealand. University of Canterbury. Christchurch. Google Scholar

15.

H. J. Bishop 1940. The bush locust (Phymateus leprosus) in the Eastern Cape Province. South Africa Department of Agriculture and Forestry Bulletin 208:1–10. Google Scholar

16.

W. U. Blanckenhorn 2000. The evolution of body size: what keeps organisms small. Quarterly Review of Biology 75:385–407. Google Scholar

17.

W. U. Blanckenhorn 2005. Behavioral causes and consequences of sexual size dimorphism. Ethology 111:977–1016. Google Scholar

18.

M. S. Blum 1981. Chemical Defenses of Arthropods. Academic Press. New York. Google Scholar

19.

M. S. Blum, R. F. Severson, R. F. Arrendale, D. W. Whitman, P. Escoubas, O. Adeyeye, and C. G. Jones . 1990. A generalist herbivore in a specialist mode: metabolic, sequestrative, and defensive consequences. Journal of Chemical Ecology 16:223–244. Google Scholar

20.

C. E. Bock, J. H. Bock, and M. C. Grant . 1992. Effects of bird predation on grasshopper densities in an Arizona grassland. Ecology 73:1706–1717. Google Scholar

21.

J. T. Bonner 2006. Why Size Matters. Princeton University Press. Princeton. Google Scholar

22.

L. P. Bower 1984. Chemical defense in butterflies. pp 109–134. In R. J. Vane-Wright and P. R. Ackery , editors. (Eds). The Biology of Butterflies. Academic Press. New York. Google Scholar

23.

A. Brindle 1970. Dermaptera. La faune terrestre de l'île de Sainte-Helene. Annales du Musee Royal de l'Afrique Centrale Tervuren. Series no 8, Sciences Zoologiques 1:213–227. Google Scholar

24.

P. A. Brodmann and H-U. Reyer . 1999. Nestling provisioning in water pipits (Anthus spinoletta): do parents go for specific nutrients or profitable prey. Oecologia 120:506–514. Google Scholar

25.

H. C. Bryant 1912. Birds in relation to grasshopper outbreak in California. University of California Publications in Zoology 11:1–20. Google Scholar

26.

M. Burrows and O. Morris . 2003. Jumping and kicking in bush crickets. Journal of Experimental Biology 206:1035–1049. Google Scholar

27.

M. P. Calcagno, J. L. Avila, I. Rudman, L. D. Otero, and M. E. Alonso-Amelot . 2004. Food-dependent regurgitate effectiveness in the defence of grasshoppers against ants: the case of bracken-fed Abracris flavolineata (Orthoptera: Acrididae). Physiological Entomology 29:123–128. Google Scholar

28.

W. A. Calder 1996. Size, Function, and Life History. Dover. Mineola, New York. Google Scholar

29.

J. L. Capinera, R. D. Scott, and T. J. Walker . 2004. Field Guide to Grasshoppers, Katydids, and Crickets of the United States. Cornell University Press. Ithaca, NY. Google Scholar

30.

C. S. Carbonell and A. Mesa . 1972. Dos nuevos géneros y especies de acridoideos andinos (Orthoptera). Revista Peruana de Entomologia 15:95–102. Google Scholar

31.

C. S. Carbonell 1986. Revision of the Neotropical genus Tropidacris (Orthoptera, Acridoidea, Romaleidae, Romaleinae). Proceedings Academy of Natural Sciences of Philadelphia 138:366–402. Google Scholar

32.

T. J. Case 1978. A general explanation for insular body size trends in terrestrial vertebrates. Ecology 59:1–18. Google Scholar

33.

J. A. Chapman and G. A. Feldhamer . 1982. Wild Mammals of North America. John Hopkins University Press. Baltimore. Google Scholar

34.

R. F. Chapman and W. W. Page . 1979. Factors affecting the mortality of the grasshopper, Zonocerus variegates, in southern Nigeria. Journal of Animal Ecology 48:271–288. Google Scholar

35.

X. Chen, C. R. Dickman, and M. B. Thompson . 2004. Selective consumption by predators of different body regions of prey: is rate of energy intake important. Journal of Zoology, London 264:189–196. Google Scholar

36.

A. J. Cherrill and M. Begon . 1989. Predation on grasshoppers by spiders in sand dune grasslands. Entomologia experimentalis et applicata 50:225–231. Google Scholar

37.

L. Chopard 1943. Orthoptèroïdes de L'Afrique du Nord. Faune L'Empire Français I 1–450. Google Scholar

38.

S. L. Chown and S. W. Nicolson . 2004. Insect Physiological Ecology Mechanisms and Patterns. Oxford University Press. Oxford. Google Scholar

39.

S. Churchfield and L. Rychlik . 2006. Diets and coexistence in Neomys and Sorex shrews in Bialowieza forest, eastern Poland. Journal of Zoology, London 269:381–390. Google Scholar

40.

S. Churchfield, J. Hollier, and V. K. Brown . 1991. The effects of small mammal predators on grassland invertebrates, investigated by field exclosure experiments. Oikos 60:283–290. Google Scholar

41.

J. L. Cloudsley-Thompson 1980. Tooth and Claw Defensive Strategies in the Animal World. J. M. Dent & Sons. London. Google Scholar

42.

R. Cogni, A. V. L. Freitas, and B. F. Amaral Filho . 2002. Influence of prey size on predation success by Zelus longipes L. (Het., Reduviidae). Journal of Applied Entomology 126:74–78. Google Scholar

43.

J. E. Cohen, S. L. Pimm, P. Yodzis, and J. Saldaña . 1993. Body sizes of animal predators and animal prey in food webs. Journal of Animal Ecology 62:67–78. Google Scholar

44.

L. C. Coleman 1911. The Jola or Deccan grasshopper (Colemania sphenarioides, Bol.). Bulletin Department of Agriculture, Mysore No 2:1–43. Google Scholar

45.

W. E. Cooper Jr., R. A. Anderson, and W. G. Federick . 2007. Prey size selection under simultaneous choice by the broad-headed skink (Eumeces laticeps). Ethology 113:417–425. Google Scholar

46.

J. T. Costa 2006. The Other Insect Societies. Harvard University Press. Cambridge. Google Scholar

47.

J. J. Craighead and F. O. Craighead . 1956. Hawks, Owls, and Wildlife. Stackpole. Harrisburg, PA, USA. Google Scholar

48.

D. C. Culver 1982. Cave Life. Harvard University Press. Cambridge, MA. Google Scholar

49.

E. Curio 1976. The Ethology of Predation. Springer-Verlag. Berlin. Google Scholar

50.

O. Dangles, D. Pierre, J. P. Christides, and J. Casas . 2007. Escape performance decreases during ontogeny in wild crickets. Journal of Experimental Biology 210:3165–3170. Google Scholar

51.

B. J. Danner and A. Joern . 2003. Stage-specific behavioral responses of Ageneotettix deorum (Orthoptera: Acrididae) in the presence of lycosid spider predators. Journal of Insect Behavior 16:453–464. Google Scholar

52.

B. J. Danner and A. Joern . 2004. Development, growth, and egg production of Ageneotettix deorum (Orthoptera: Acrididae) in response to spider predation risk and elevated resource quality. Ecological Entomology 29:1–11. Google Scholar

53.

M. R. Delvi and T. J. Pandian . 1979. Ecological energetics of the grasshopper Poecilocerus pictus in Bangalore fields. Proceedings Indian Academy of Sciences 88:241–256. Google Scholar

54.

J. P. Dempster 1967. The control of Pieris rapae with DDT. I. The natural mortality of the young stages of Pieris. Journal of Applied Ecology 4:485–500. Google Scholar

55.

D. S. Dennis and R. J. Lavigne . 1985. Comparative behavior of Wyoming robber flies II. (Diptera: Asilidae). University Wyoming Agriculture Experiment Station Science Monograph 30:1–68. Google Scholar

56.

M. Descamps and D. Wintrebert . 1966. Pyrgomorphidae et Acrididae de Madagascar. Observations biologiques et diagnoses (Orth., Acridoidea). EOS Revista Espanola de Entomologia 42:41–263. Google Scholar

57.

E. Despland and S. J. Simpson . 2005. Food choices of solitarious and gregarious locusts reflect cryptic and aposematic antipredator strategies. Animal Behaviour 69:471–479. Google Scholar

58.

C. R. Dickman 1988. Body size, prey size, and community structure in insectivorous mammals. Ecology 69:569–580. Google Scholar

59.

V. M. Dirsh 1962. The Acridoidea (Orthoptera) of Madagascar I. Acrididae (except Acridinae). Bulletin of the British Museum (Natural History) Entomology 12:25–350. Google Scholar

60.

V. M. Dirsh 1963a. The Acridoidea (Orthoptera) of Madagascar II. Acrididae, Acridinae. Bulletin of the British Museum (Natural History) Entomology 13:245–286. Google Scholar

61.

V. M. Dirsh 1963b. The Acridoidea (Orthoptera) of Madagascar III. Pyrgomorphidae. Bulletin of the British Museum (Natural History) Entomology 14:51–103. Google Scholar

62.

V. M. Dirsh 1966. Acridoidae of Angola I & II. Museu do Dundo. Lisbon. Google Scholar

63.

V. M. Dirsh 1970. Acridoidea of the Congo (Orthoptera). Musee Royal de L'Afrique Centrale. Tervuren, Belgique Annales. Serie IN-8. Sciences Zoologiques no 182:1–605. Google Scholar

64.

A. F. G. Dixon 1959. An experimental study of the searching behavior of the predatory coccinellid beetle Adalia decempunctata (L.). Journal of Animal Ecology 28:259–281. Google Scholar

65.

A. F. G. Dixon and J-L. Hemptinne . 2001. Body size distribution in predatory ladybird beetles reflects that of their prey. Ecology 82:1847–1856. Google Scholar

66.

A. F. G. Dixon and R. J. Russell . 1972. The effectiveness of Anthocoris nemorum and A. confusus as predators of the sycamore aphid Drepanosiphum platanoides. II. Searching behavior and the incidence of predation in the field. Entomologia experimentalis et Applicata 15:5–50. Google Scholar

67.

S. M. Dixon and R. L. Baker . 1988. Effects of size on predation risk, behavioural response to fish, and cost of reducing feeding in larval Iscnura verticalis (Coenagrionidae: Odonata). Oecologia 76:200–205. Google Scholar

68.

E. B. Dopman, G. A. Sword, and D. M. Hillis . 2002. The importance of the ontogenetic niche in resource-associated divergence: evidence from a generalist grasshopper. Evolution 56:731–740. Google Scholar

69.

B. A. C. Dudley 1961. Studies on the biology of locusts when reared under controlled conditions. Ph.D. Thesis, Cardiff. Google Scholar

70.

R. Dudley 2000. The Biomechanics of Insect Flight. Princeton University Press. Princeton. Google Scholar

71.

R. Dudley 2002. Mechanisms and implications of animal flight maneuverability. Integrative and Comparative Biology 42:135–140. Google Scholar

72.

M. Edmunds 1974. Defence in Animals. Longman. Harlow, UK. Google Scholar

73.

T. Eisner, L. B. Hendry, D. B. Peakall, and J. Meinwald . 1971. 2,5-Dichlorophenol (from ingested herbicide?) in defensive secretion of grasshopper (Romalea microptera: Orthoptera: Acrididae). Science 172:277–278. Google Scholar

74.

T. Eisner, M. Eisner, and M. Siegler . 2005. Secret Weapons. Belknap Press. Cambridge. Google Scholar

75.

S. B. Emerson, H. W. Greene, and E. L. Charnov . 1994. Allometric aspects of predator–prey interactions. pp 123–139. In S. M. Reilly , editor. (Ed.). Ecological Morphology: Integrative Organismal Biology. University of Chicago Press. Chicago. Google Scholar

76.

F. Enders 1975. The influence of hunting manner on prey size, particularly in spiders with long attack distances (Araneidae, Linyphiidae and Salticidae). American Naturalist 109:737–763. Google Scholar

77.

J. A. Endler 1985. Natural Selection in the Wild. Princeton University Press. Princeton. Google Scholar

78.

J. A. Endler 1986. Defense against predators. pp 109–134. In M. E. Feder and G. V. Lauder , editors. (Eds). Predator-Prey Relationships. University of Chicago Press. Chicago. Google Scholar

79.

J. A. Endler 1991. Interactions between predators and prey. pp 169–201. In J. R. Krebs and N. B. Davies , editors. (Eds). Behavioural Ecology an Evolutionary Approach. 3rd EdBlackwell. London. Google Scholar

80.

Jv Euw, L. Fishelson, J. A. Parsons, T. Reichstein, and M. Rothschild . 1967. Cardenolides (heart poisons) in a grasshopper feeding on milkweeds. Nature 214:35–39. Google Scholar

81.

D. L. Evans and J. O. Schmidt . 1990. Insect Defenses. State University of New York Press. Albany. Google Scholar

82.

N. Evenhuis and L. Eldredge . 2004. Natural History of Nihoa and Necker Islands. Bishop Museum Press. Honolulu. Google Scholar

83.

A. Exnerova, P. Stys, A. Kristin, O. Volf, and M. Pudil . 2003. Birds as predators of true bugs (Heteroptera) in different habitats. Biologia (Bratislava) 58:253–264. Google Scholar

84.

K. Falk, F. P. Jensen, K. D. Christensen, and B. S. Petersen . 2006. The diet of nestling Abdim's stork Ciconia abdimii in Niger. Waterbirds 29:215–220. Google Scholar

85.

P. Feeny, W. S. Blau, and P. M. Kareiva . 1985. Larval growth and survivorship of the black swallowtail butterfly in central New York. Ecological Monographs 55:167–187. Google Scholar

86.

E. Fichter, G. Schildman, and J. H. Sather . 1955. Some feeding patterns of coyotes in Nebraska. Ecological Monographs 25:1–37. Google Scholar

87.

L. Fishelson 1960. The biology and behavior of Poekilocerus bufonius Klug, with special reference to the repellent gland (Orth. Acrididae). EOS Revista Espanola de Entomologia (Madrid) 36:41–62. Google Scholar

88.

A. Forsman and S. Merilaita . 1999. Fearful symmetry: pattern size and asymmetry affects aposematic signal efficacy. Evolutionary Ecology 13:131–140. Google Scholar

89.

J. B. Foster 1964. Evolution of mammals on islands. Nature 202:234–235. Google Scholar

90.

E. Lichter, G. Schildman, and J. H. Sather . 1955. Some feeding patterns of coyotes in Nebraska. Ecological Monographs 25:1–37. Google Scholar

91.

A. C. Fowler, R. L. Knight, T. L. George, and L. C. McEwen . 1991. Effects of avian predation on grasshopper populations in North Dakota grasslands. Ecology 72:1775–1781. Google Scholar

92.

R. J. Full, T. Kubow, J. Schmitt, P. Holmes, and D. Koditschek . 2002. Quantifying dynamic stability and maneuverability in legged locomotion. Integrative and Comparative Biology 42:149–157. Google Scholar

93.

G. Gäde 2002. Sexual dimorphism in the pyrgomorphid grasshopper Phymateus morbillosus: from wing morphometry and flight behaviour to flight physiology and endocrinology. Physiological Entomology 27:51–57. Google Scholar

94.

G. Gamberale and B. S. Tullberg . 1998. Aposematism and gregariousness: the combined effect of group size and coloration on signal repellence. Proceedings Royal Society of London, Series B 265:889–894. Google Scholar

95.

K. T. Gardner and D. C. Thompson . 1998. Influence of avian predation on a grasshopper (Orthoptera: Acrididae) assemblage that feeds on threadleaf snakeweed. Environmental Entomology 27:110–116. Google Scholar

96.

G. W. Gibbs 1998. Why are some weta (Orthoptera: Stenopelmatidae) vulnerable yet others are common. Journal of Insect Conservation 2:161–166. Google Scholar

97.

H. R. Goerlitz and B. M. Siemers . 2007. Sensory ecology of prey rustling sounds: acoustical features and their classification by wild Grey Mouse Lemurs. Functional Ecology 21:143–153. Google Scholar

98.

D. J. Greathead 1966. A brief survey of the effects of biotic factors on populations of the desert locust. Journal of Applied Ecology 3:239–250. Google Scholar

99.

D. Griffiths 1980. Foraging costs and relative prey size. American Naturalist 116:743–752. Google Scholar

100.

F. R. Groeters and K. L. Strong . 1993. Observations on distastefulness of Monistria concinna (Walker) (Orthoptera: Pyrgomorphidae). Journal of the Australian Entomology Society 32:153–154. Google Scholar

101.

T. Guilford 1990. The evolution of aposematism. pp 23–61. In D. L. Evans and J. O. Schmidt , editors. (Eds). Insect Defenses Adaptive Mechanisms and Strategies of Prey and Predators. State University of New York Press. Albany. Google Scholar

102.

P. H. Harvey and P. J. Greenwood . 1978. Antipredator defence strategies: some evolutionary problems. pp 129–151. In J. R. Krebs and N. B. Davies , editors. (Eds). Behavioural Ecology an Evolutionary Approach. Blackwell. Oxford. Google Scholar

103.

K. Harz 1975. Die Orthopteren Europas II. W. Junk B.V. The Hague. Google Scholar

104.

J. D. Hatle and S. G. Faragher . 1998. Slow movement increases the survivorship of a chemically defended grasshopper in predatory encounters. Oecologia 115:260–267. Google Scholar

105.

J. D. Hatle and D. W. Whitman . 2001. Sluggish movement of conspicuous insects as a defense mechanism against motion-oriented predators. pp 209–228. In T. N. Ananthakrishnan , editor. (Ed.). Insects and Plant Defence Dynamics. Science Publisheers. Enfield, NH, USA. Google Scholar

106.

J. D. Hatle, B. A. Salazar, and D. W. Whitman . 2002. Survival advantage of sluggish individuals in aggregations of aposematic prey, during encounters with ambush predators. Evolutionary Ecology 16:415–431. Google Scholar

107.

M. Hebard 1925a. A revision of the genus Taeniopoda (Orthoptera, Acrididae, Cyrtacanthacrinae). Transactions American Entomological Society (Philadelphia) 50:253–274. Google Scholar

108.

M. Hebard 1925b. The group Taeniopodae as found in the United States (Orthoptera). Transactions American Entomological Society (Philadelphia) 52:1–12. Google Scholar

109.

B. Heinrich 1993. How avian predators constrain caterpillar foraging. pp 224–247. In N. E. Stamp and T. M. Casey , editors. (Eds). Caterpillars Ecological and Evolutionary Constraints on Foraging. Chapman & Hall. New York. Google Scholar

110.

J. R. Helfer 1953. How to know the Grasshoppers, Cockroaches and their Allies. WM. C. Brown. Dubuque, Iowa, USA. Google Scholar

111.

H. R. Hermann 1984. Defensive Mechanisms in Social Insects. Praeger. New York. Google Scholar

112.

B. Hölldobler and E. O. Wilson . 1990. The Ants. Harvard University Press. Cambridge, MA. Google Scholar

113.

C. S. Holling, R. L. Dunbrack, and L. M. Dill . 1976. Predator size and prey size: presumed relationship in the mantid Hierodula coarctata. Canadian Journal of Zoology 54:1760–1764. Google Scholar

114.

A. Honěk 1993. Intraspecific variation in body size and fecundity in insects: a general relationship. Oikos 66:483–492. Google Scholar

115.

A. Ichikawa, F. Ito, Y. Kano, M. Kawai, T. Murai, and O. Tominago . 2006. Orthoptera of the Japanese Archipelago in Color. Hokkaido University Press. Sapporo, Japan. [in Japanese]. Google Scholar

116.

T. Iwasaki 1991. Predatory behavior of the preying mantis, Tenodera aridifolia II. Combined effect of prey size and predator size on the prey recognition. Journal of Ethology 9:77–81. Google Scholar

117.

D. H. Janzen 1993. Caterpillar seasonality in a Costa Rican dry forest. pp 448–477. In N. E. Stamp and T. M. Casey , editors. (Eds). Caterpillars Ecological and Evolutionary Constraints on Foraging. Chapman and Hall. New York. Google Scholar

118.

R. Ji, S. J. Simpson, F. Yu, Q. X. He, and C. J. Yun . 2008. Diets of migratory rosy starlings (Passeriformes: Sturnidae) and their effects on grasshoppers: implications for a biological agent for insect pests. Biological Control 46:547–551. Google Scholar

119.

A. Joern 1986. Experimental study of avian predation on coexisting grasshopper populations (Orthoptera: Acrididae) in a sandhills grassland. Oikos 46:243–249. Google Scholar

120.

A. Joern 1992. Variable impact of avian predation on grasshopper assemblies in sandhills grassland. Oikos 64:458–463. Google Scholar

121.

P. Johnsen 1990. Acridoidea of Botswana I. Zoological Laboratory, Aarhus University. Denmark. Google Scholar

122.

P. Johnsen 1991. Acridoidea of Botswana II. Zoological Laboratory, Aarhus University. Denmark. Google Scholar

123.

C. G. Johnson, L. A. Nickerson, and M. J. Bechard . 1987. Grasshopper consumption and summer flocks of nonbreeding Swainson's hawks. Condor 89:676–678. Google Scholar

124.

C. G. Jones, T. A. Hess, D. W. Whitman, P. J. Silk, and M. S. Blum . 1987. Effects of diet breadth on autogenous chemical defense of a generalist grasshopper. Journal of Chemical Ecology 13:283–297. Google Scholar

125.

C. G. Jones, D. W. Whitman, P. J. Silk, and M. S. Blum . 1988. Diet breadth and insect chemical defenses: A generalist grasshopper and a general hypothesis. pp 477–512. In K. Spencer , editor. (Ed.). Chemical Mediation of Coevolution. Academic Press. San Diego, CA. Google Scholar

126.

C. G. Jones, D. W. Whitman, S. J. Compton, P. S. Silk, and M. S. Blum . 1989. Reduction in diet breadth results in sequestration of plant chemicals and increases efficacy of chemical defense in a generalist grasshopper. Journal of Chemical Ecology 15:1811–1822. Google Scholar

127.

C. Jones, K. Moss, and M. Sanders . 2005. Diet of hedgehogs (Erinaceus europaeus) in the upper Waitaki Basin, New Zealand: implications for conservation. New Zealand Journal of Ecology 29:29–35. Google Scholar

128.

D. A. Jones, R. J. Keymer, and W. M. Ellis . 1978. Biochemical aspects of plant and animal coevolution. pp 213–242. In J. Harborne , editor. (Ed.). Academic Press. London. Google Scholar

129.

M. Kaspari 1990. Prey preparation and the determinants of handling time. Animal Behaviour 40:118–126. Google Scholar

130.

K. N. Katiyar 1955. The life-history and ecology of the northern Spotted Grasshopper, Aularches punctatus Drury (Orhtoptera: Acrididae). Agra University Journal of Research 4:397–414. Google Scholar

131.

T. Kaufmann 1965. Observations on aggregation, migration, and feeding habitats of Zonocerus variegates in Ghana (Orthoptera: Acrididae). Annals Entomology Society of America 58:426–436. Google Scholar

132.

H. B. D. Kettlewell 1973. The Evolution of Melanism. Oxford Clarendon Press. Google Scholar

133.

K. H. L. Key 1985. Monograph of the Monistriini and Petasidini (Orthoptera: Pyrgomorphidae). Australian Journal of Zoology. Supplementary Series No 107:1–213. Google Scholar

134.

K. W. Kim, B. Krafft, and J. C. Choe . 2005. Cooperative prey capture by young subsocial spiders I. Functional value. Behavioral Ecology & Sociobiology 59:92–100. Google Scholar

135.

J. Kingdom 1997. The Kingdom Field Guide to African Mammals. Academic Press. San Deigo. Google Scholar

136.

P. F. Kukuk, G. C. Eickwort, M. Raveret-Richter, B. Alexander, R. Gibson, R. A. Morse, and F. Ratnieks . 1989. Importance of the sting in the evolution of sociality in the Hymenoptera. Annals Entomological Society of America 82:1–5. Google Scholar

137.

M. A. Lamb, D. J. Otto, and D. W. Whitman . 1999. Parasitism of Eastern Lubber grasshopper by Anisia serotina (Diptera: Tachinidae) in Florida. Florida Entomologist 82:365–371. Google Scholar

138.

M. V. Lomolino 2005. Body size evolution in insular vertebrates: generality of the island rule. Journal of Biogeography 32:1683–1699. Google Scholar

139.

H. López, M. Nogales, E. Morales, and P. Oromí . 2007. Habitat use and phenology of the large insular endemic grasshopper Acrostira euphorbiae (Orthoptera: Pamphagidae). Bulletin of Entomological Research 97:117–127. Google Scholar

140.

S. Lorenz 2007. Carolina mantid (Stagmomantis carolina) captures and feeds on a broad-tailed hummingbird (Selasphorus platycercus). Bulletin of the Texas Ornithological Society 40:37–38. Google Scholar

141.

R. H. MacArthur and E. O. Wilson . 1967. The Theory of Island Biogeography. Princeton University Press. Princeton, NJ. Google Scholar

142.

V. C. Maiorana 1981. Prey selection by sight: random or economic. American Naturalist 118:450–451. Google Scholar

143.

A. M. Makarieva, V. G. Gorshkov, and B-L. Li . 2005. Gigantism, temperature and metabolic rate in terrestrial poikilotherms. Proceedings of the Royal Society B 272:2325–2328. Google Scholar

144.

E. J. Maly 1970. The influence of predation on the adult sex ratios of two copepod species. Limnology and Oceanography 15:566–573. Google Scholar

145.

T. Mänd, T. Tammaru, and J. Mappes . 2007. Size dependent predation risk in cryptic and conspicuous insects. Evolutionary Ecology 21:485–498. Google Scholar

146.

R. B. Matlock Jr. 2005. Impact of prey size on prey capture success, development rate, and survivorship in Perillus bioculatus (Heteroptera: Pentatomidae), a predator of the Colorado potato beetle. Environmental Entomology 34:1048–1056. Google Scholar

147.

W. J. Mattson, F. B. Knight, D. C. Allen, and J. L. Foltz . 1968. Vertebrate predation on the jack-pine budworm in Michigan. Journal Economic Entomology 61:229–234. Google Scholar

148.

P. J. Mayhew 2006. Discovering Evolutionary Ecology. Oxford University Press. Oxford. Google Scholar

149.

E. Mayr 1956. Geographical character gradients and climatic adaptation. Evolution 10:105–108. Google Scholar

150.

D. I. McCracken, E. M. Bignal, S. Blake, and G. N. Foster . 2004. Productivity and profitability: the effects of farming practices on the prey of insectivorous birds. pp 75–87. In H. F. van Emden and M. Roschild , editors. (Eds). Insect and Bird Interactions. Intercept. Andover, UK. Google Scholar

151.

A. McLachlan, R. Ladle, and B. Crompton . 2003. Predator-prey interactions on the wing: aerobatics and body size among dance flies and midges. Animal Behaviour 66:911–915. Google Scholar

152.

R. F. Medina and P. Barbosa . 2002. Predation of small and large Orgyia leucostigma (J. E. Smith) (Lepidoptera: Lymantriidae) larvae by vertebrate and invertebrate predators. Environmental Entomology 31:1097–1102. Google Scholar

153.

S. Meiri, D. Tamar, and D. Simberloff . 2006. The generality of the island rule re-examined. Journal of Biogeography 33:1571–1577. Google Scholar

154.

E. L. Mockford 1992. Taxonomy of the thyrosphorine barklice of Panama (Psocoptera: Psocidae: Thyrsophorinae. pp 257–270. In D. Quintero and A. Aiello , editors. (Eds). Insects of Panama and Mesoamerica. Oxford Science Publications. Oxford. Google Scholar

155.

E. L. Mockford 1993. North American Psocoptera (Insecta). Sandhill Crane Press. Gainesville, FL. Google Scholar

156.

C. B. Montllor and E. A. Bernays . 1993. Invertebrate predators and caterpillar foraging. pp 170–202. In N. E. Stamp and T. M. Casey , editors. (Eds). Caterpillars Ecological and Evolutionary Constraints on Foraging. Chapman and Hill. New York. Google Scholar

157.

I. Montoya and K. C. Burns . 2007. Community-wide character displacement in New Zealand skinks. Journal of Biogeography 34:2139–2147. Google Scholar

158.

P. J. Morin 1984. The impact of fish exclusion on the abundance and species composition of larval odonates: results of short-term experiments in a North Carolina farm pond. Ecology 65:53–60. Google Scholar

159.

R. F. Morris 1963. The effects of predator age and prey defense on the functional response of Podisus maculiventris Say to the density of Hyphantria cunea Drury. Canadian Entomologist 95:1009–1020. Google Scholar

160.

W. Nentwig and C. Wissel . 1986. A comparison of prey lengths among spiders. Oecologia 68:595–600. Google Scholar

161.

T. R. New 1991. Insects as Predators. New South Wales University Press. Kensington, Australia. Google Scholar

162.

M. Nilsson and A. Forsman . 2003. Evolution of conspicuous coloration, body size and gregariousness: a comparative analysis of lepidopteran larvae. Evolutionary Ecology 17:51–66. Google Scholar

163.

A. P. Norman 1995. Adaptive changes in locust kicking and jumping behaviour during development. Journal of Experimental Biology 198:1341–1350. Google Scholar

164.

S. Nylin and K. Gotthard . 1998. Plasticity in life-history traits. Annual Review of Entomology 43:63–83. Google Scholar

165.

W. J. O'Brien, N. A. Slade, and G. L. Vinyard . 1976. Apparent size as the determinant of prey selection by bluegill sunfish (Lepomis macrochirus). Ecology 57:1304–1310. Google Scholar

166.

T. Okuyama 2007. Prey of two species of jumping spiders in the field. Applied Entomology and Zoology 42:663–668. Google Scholar

167.

R. M. Olberg, A. H. Worthington, J. L. Fox, C. E. Bessette, and M. P. Loosemore . 2005. Prey size selection and distance estimation in foraging adult dragonflies. Journal of Comparative Physiology A 191:791–797. Google Scholar

168.

J. C. Ortega 1987. Coyote food habits in southeastern Arizona. Southwestern Naturalist 32:152–156. Google Scholar

170.

O. Ovadia and O. J. Schmitz . 2002. Linking individuals with ecosystems: experimentally identifying the relevant organizational scale for predicting trophic abundances. Proceedings National Academy of Sciences 99:12927–12931. Google Scholar

171.

N. Owen-Smith and M. G. L. Mills . 2008. Predator-prey size relationships in an African large-mammal food web. Journal of Animal Ecology 77:173–183. Google Scholar

172.

R. T. Paine 1976. Size-limited predation: an observational and experimental approach with the Mytilus-Pisaster interaction. Ecology 57:858–873. Google Scholar

173.

J. M. Pasteels and J-C. Grégoire . 1983. The chemical ecology of defense in arthropods. Annual Review of Entomology 28:263–289. Google Scholar

174.

D. L. Pearson 1985. The function of multiple antipredator mechanisms in adult tiger beetles (Coleoptera: Cicindelidae). Ecological Entomology 10:65–72. Google Scholar

175.

D. L. Pearson and E. J. Mury . 1979. Character divergence and convergence among tiger beetles (Coleoptera: Cicindelidae). Ecology 60:557–566. Google Scholar

176.

R. H. Peters 1983. The Ecological Implications of Body Size. Cambridge University Press. Cambridge. Google Scholar

177.

R. E. Pfadt 1994. Field Guide to Common Western Grasshoppers. Wyoming Agricultural Experiment Station. Bulletin 912. Google Scholar

178.

J. Phipps 1962. The ovaries of some Sierra Leone Acridoidea (Orthoptera) with some comparisons between east and west African forms. Proceedings Royal Society of London, Series A 37:13–21. Google Scholar

179.

A. Polanowski, M. S. Blum, D. W. Whitman, and J. Travis . 1997. Proteinase inhibitors in the nonvenomous defensive secretion of grasshoppers: antiproteolytic range and possible significance. Comprehensive Biochemistry and Physiology 117B:525–529. Google Scholar

180.

K. Preston-Mafham 1990. Grasshoppers and Mantids of the World Facts on File, New York. Google Scholar

181.

D. Priddell, N. Carlile, M. Humphrey, S. Fellenberg, and D. Hiscox . 2003. Rediscovery of the ‘extinct’ Lord Howe Island Stick-insect (Dryococelus australis (Montrouzier)) (Phasmatodea) and recommendations for its conservation. Biodiversity & Conservation 12:1391–1403. Google Scholar

182.

N. Prop 1960. Protection against birds and parasites in some species of tenthredinid larvae. Archives Néerlandaises de Zoologie 13:380–447. Google Scholar

183.

K. L. Prudic, A. K. Skemp, and D. R. Papaj . 2007. Aposematic coloration, luminance contrast, and the benefits of conspicuousness. Behavioral Ecology 18:41–46. Google Scholar

184.

H. Radclyffe Roberts and C. S. Carbonell . 1982. A revision of the grasshopper genera Chromacris and Xestotrachelus (Orthoptera, Romaleidae, Romaleinae). Proceedings California Academy of Sciences 43:43–58. Google Scholar

185.

F. G. T. Radloff and J. T. Du Toit . 2004. Large predators and their prey in a southern African savanna: a predator's size determines its prey size range. Journal of Animal Ecology 73:410–423. Google Scholar

186.

P. Raia and S. Meiri . 2006. The island rule in large mammals: paleontology meets ecology. Evolution 60:1731–1742. Google Scholar

187.

J. C. Ray and M. E. Sunquist . 2001. Trophic relations in a community of African rainforest carnivores. Oecologia 127:395–408. Google Scholar

188.

D. Reavey 1993. Why body size matters to caterpillars. pp 248–279. In N. E. Stamp and T. M. Casey , editors. (Eds). Caterpillars Ecological and Evolutionary Constraints on Foraging. Chapman and Hall. New York. Google Scholar

189.

J. A. G. Rehn and H. G. Grant . 1959. A review of the Romaleinae (Orthoptera; Acrididae) found in America north of Mexico. Proceedings Academy of Natural Sciences Philadelphia 111:109–271. Google Scholar

190.

J. A. G. Rehn and H. G. Grant . 1961. A monograph of the Orthoptera of North America. Volume I. Monographs of the Academy of Natural Sciences of Philadelphia No 12:1–257. Google Scholar

191.

D. Roff 1981. On being the right size. American Naturalist 118:405–422. Google Scholar

192.

D. Roff 2002. Life History Evolution. Sinauer. Sunderland, MA, USA. Google Scholar

193.

J. Roffey 1979. Locusts and grasshoppers of economic importance in Thailand. Anti-Locust Memoir 14:1–200. Google Scholar

194.

M. Rothschild 1973. British aposematic Lepidoptera. pp 9–62. In J. H. Heath and A. M. Emmet , editors. (Eds). The Moths and Butterflies of Great Britain and Ireland. Harley Books. Essex, England. Google Scholar

195.

C. H. F. Rowell 1967. Experiments on aggregations of Phymateus purpurascens (Orthoptera, Acrididae, Pyrgomorphinae). Journal of Zoology 152:179–193. Google Scholar

196.

H. F. Rowell 1983. Tropidacris cristata (Saltamonte o chapulín gigante, giant red-winged grasshopper. pp 772–773. In D. H. Janzen , editor. (Ed.). Costa Rican Natural History. The University of Chicago Press. Chicago. Google Scholar

197.

G. D. Ruxton, T. N. Sherratt, and M. P. Speed . 2004. Avoiding Attack: The Evolutionary Ecology of Crypsis, Warning Signals & Mimicry. Oxford University Press. Oxford. Google Scholar

198.

M. W. Sabelis 1992. Predatory arthropods. pp 225–264. In M. J. Crawley , editor. (Ed.). Natural Enemies. Blackwell. Oxford. Google Scholar

199.

B. A. Salazar and D. W. Whitman . 2001. Defensive tactics of caterpillars against predators and parasitoids. pp 161–207. In T. N. Ananthakrishnan , editor. (Ed.). Insect and Plant Defense Dynamics. Science Publishers. Enfield, NH, USA. Google Scholar

200.

L. Salvati, L. Ranazzi, and A. Manganaro . 2001. Cicadas (Cicadidae) as alternative prey in the diet of urban Tawny Owls Strix aluco. Biota (Race) 2:187–190. Google Scholar

201.

A. C. Scarborough 1978. Ethology of Cerotainia albipilosa Curran (Diptera: Asilidae) in Maryland: predatory behavior. Proceedings Entomological Society of Washington 80:113–127. Google Scholar

202.

D. Schluter, T. D. Price, and L. Rowe . 1991. Conflicting selection pressures and life history trade-offs. Proceedings Royal Society of London, Series B 246:11–17. Google Scholar

203.

J. O. Schmidt 1990. Hymenopteran venoms: striving toward the ultimate defense against vertebrates. pp 387–419. In D. Evans and J. Schmidt , editors. (Eds). Arthropod Defenses Adaptive Mechanisms and Strategies of Prey and Predators. State University of New York Press. Albany, New York. Google Scholar

204.

K. Schmidt-Nielsen 1984. Scaling: Why is Animal Size so Important. Cambridge University Press. Cambridge. Google Scholar

205.

N. Schülert and U. Dicke . 2002. The effect of stimulus features on the visual orienting behaviour of the salamander Plethodon jordani. Journal of Experimental Biology 205:241–251. Google Scholar

206.

J. C. Schultz 1981. Adaptive changes in antipredator behavior of a grasshopper during development. Evolution 35:175–179. Google Scholar

207.

T. E. Shelly and D. L. Pearson . 1980. Predatory behavior of Proctacanthella leucopogon (Diptera: Asilidae): prey recognition and prey records. Environmental Entomology 9:7–9. Google Scholar

208.

R. Shine and J. Thomas . 2005. Do lizards and snakes really differ in their ability to take large prey? A study of relative prey mass and feeding tactics in lizards. Oecologia 144:492–498. Google Scholar

209.

S. J. Simpson and G. A. Sword . 2009. Phase polyphenism in locusts: mechanisms, population consequences, adaptive significance and evolution. pp 147–190. In D. W. Whitman and T. N. Ananthakrishnan , editors. (Eds). Phenotypic Plasticity of Insects: Mechanisms and Consequences. Science Publishers. Enfield, NJ. Google Scholar

210.

A. R. E. Sinclair, S. Mduma, and J. S. Brashares . 2003. Patterns of predation in a diverse predator-prey system. Nature 425:288–290. Google Scholar

211.

M. Slatkin 1984. Ecological causes of sexual dimorphism. Evolution 38:622–630. Google Scholar

212.

J. J. Sloggett 2008. Weighty matters: body size, diet and specialization in aphidophagous ladybird beetles (Coleoptera: Coccinellidae). European Journal of Entomology 105:381–389. Google Scholar

213.

F. A. Smith 1992. Evolution of body size among wood rats from Baja California, Mexico. Functional Ecology 6:265–273. Google Scholar

214.

K. D. Smith and G. B. Popov . 1953. On birds attacking desert locust swarms in Eritea. Entomologist 86:3–7. Google Scholar

215.

M. E. Snook, M. S. Blum, D. W. Whitman, R. F. Arrendale, C. E. Costello, and J. S. Hartwood . 1993. Caffeoyltartronic acid from catnip (Nepeta cataria): a precursor for catechol in lubber grasshopper (Romalea guttata) defensive secretions. Journal of Chemical Ecology 19:1957–1966. Google Scholar

216.

A. L. T. Souza, M. O. Gonzaga, and J. Vasconcellos-Neto . 2007. Prey capture behavior in the social spider Anelosimus eximius (Araneae: Theridiidae): responses to prey size and type. Ethology 113:856–861. Google Scholar

217.

C. K. Starr 1985. Enabling mechanisms in the origin of sociality in the Hymenoptera: the sting's the thing. Annals Entomological Society of America 78:836–840. Google Scholar

218.

T. W. Stauffer and D. W. Whitman . 2007. Divergent oviposition behaviors in a desert vs a marsh grasshopper. Journal of Orthoptera Research 16:103–114. Google Scholar

219.

S. C. Stearns 1992. The Evolution of Life Histories. Oxford University Press. Oxford. Google Scholar

220.

D. W. Stephens and J. R. Krebs . 1986. Foraging Theory. Princeton University Press. Princeton, NJ. Google Scholar

221.

D. G. Steyn 1962. Grasshopper (Phymateus leprosus Fabr.) poisoning in a Bantu child. South African Medical Journal 36:822–823. Google Scholar

222.

C. W. Stortenbeker 1967. Observations on the population dynamics of the Red Locust, Nomadacris septemfasciata (Serville), in its outbreak areas. Agricultural Research Reports (Centre for Agricultural Publications and Documentation, Wageningen) No 694:1–118. Google Scholar

223.

W. J. Stower and D. J. Greathead . 1969. Numerical changes in a population of the desert locust, with special reference to factors responsible for mortality. Journal of Applied Ecology 6:203–235. Google Scholar

224.

D. P. Swain 1992. Selective predation for vertebral phenotype in Gasterosteus aculeatus: reversal in the direction of selection at different larval sizes. Evolution 46:998–1013. Google Scholar

225.

G. A. Sword 1999. Density-dependent warning coloration. Nature 397:217. Google Scholar

226.

G. A. Sword 2000. Locusts, lizards and lymph nodes (conclusion). Metaleptea (Newsletter of the Orthopterists' Society) 20:7. Google Scholar

227.

G. A. Sword 2001. Tasty on the outside, but toxic in the middle: grasshopper regurgitation and host plant-mediated toxicity to a vertebrate predator. Oecologia 128:416–421. Google Scholar

228.

D. J. Thompson and O. M. Fincke . 2002. Body size and fitness in Odonata, stabilizing selection and a meta-analysis too far. Ecological Entomology 27:378–384. Google Scholar

229.

L. Tinbergen 1960. The natural control of insects in pinewoods. I. Factors influencing the intensity of predation by songbirds. Archives Néerlandaises de Zoologie 13:265–343. Google Scholar

230.

T. A. Troost, B. W. Kooi, and U. Dieckmann . 2008. Joint evolution of predator body size and prey-size preference. Evolutionary Ecology 22:771–799. Google Scholar

231.

B. Uvarov 1966. Grasshoppers and Locusts. Vol. I.Cambridge University Press. London. Google Scholar

232.

B. Uvarov 1977. Grasshoppers and Locusts. Vol. II.Centre for Overseas Pest Research. London. Google Scholar

233.

G. J. Vermeij 1982. Unsuccessful predation and evolution. American Midland Naturalist 120:701–720. Google Scholar

234.

V. R. Vickery and D. K. Mc E. Kevan . 1985. The grasshoppers, crickets, and related insects of Canada and adjacent regions. Research Branch Agriculture Canada Publication 1777:1–918. Google Scholar

235.

S. E. Vincent 2006. Sex-based divergence in head shape and diet in the Eastern Lubber grasshopper (Romalea microptera). Zoology: Analysis of Complex Systems 109:331–338. Google Scholar

236.

S. E. Vincent and A. Herrel . 2007. Functional and ecological correlates of ecological dimorphisms in squamate reptiles. Integrative and Comparative Biology 47:172–188. Google Scholar

237.

S. E. Vincent and S. P. Lailvaux . 2008. Does phenotypic integration constrain sexual size dimorphism in eastern lubber grasshoppers (Romalea microptera). Journal of Orthoptera Research 17:219–225. Google Scholar

238.

K. Vulinec 1990. Collective security: aggregation by insects as a defense. pp 251–288. In D. L. Evans and J. O. Schmidt , editors. (Eds). Insect Defenses Adaptive Mechanisms and Strategies of Prey and Predators. State University of New York Press. Albany. Google Scholar

239.

D. M. Ware 1972. Predation by rainbow trout (Salmo gairdneri): the influence of hunger, prey density, and prey size. Journal Fisheries Research Board Canada 29:1193–1201. Google Scholar

240.

P. H. Warren and J. H. Lawton . 1987. Invertebrate predator-prey body size relationships: an explanation for upper triangular food webs and patterns in food web structure. Oecologia 74:231–235. Google Scholar

241.

M. Watanabe 1976. A preliminary study on population dynamics of the swallowtail butterfly, Papilio xuthus L. in a deforested area. Researches on Population Ecology 17:200–210. Google Scholar

242.

M. Watanabe 1981. Population dynamics of the swallowtail butterfly Papilo xuthus. L. in a deforested area. Researches on Population Ecology 23:74–93. Google Scholar

243.

C. P. Wheater 1988. Predator-prey size relationships in some Pterostichini (Coleoptera: Carabidae). Coleopterists Bulletin 42:237–240. Google Scholar

244.

M. J. Whiting, L. T. Reaney, and J. S. Keogh . 2007. Ecology of Wahlberg's velvet gecko, Homopholis wahlbergii, in southern Africa. African Zoology 42:38–44. Google Scholar

245.

D. W. Whitman 1986. Laboratory biology of Taeniopoda eques (Orthoptera: Acrididae). Journal of Entomological Science 21:87–93. Google Scholar

246.

D. W. Whitman 1987. Thermoregulation and daily activity patterns in a black desert grasshopper, Taeniopoda eques. Animal Behaviour 35:1814–1826. Google Scholar

247.

D. W. Whitman 1988. Allelochemical interactions among plants, herbivores, and their predators. pp 11–64. In P. Barbosa and D. Letourneau , editors. (Eds). Novel Aspects of Insect-Plant interactions. Wiley. New York. Google Scholar

248.

D. W. Whitman 1988. Function and evolution of thermoregulation in the desert grasshopper Taeniopoda eques. Journal of Animal Ecology 57:369–383. Google Scholar

249.

D. W. Whitman 1990. Grasshopper chemical communication. pp 357–391. In R. F. Chapman and A. Joern , editors. (Eds). Biology of Grasshoppers. Wiley. New York. Google Scholar

250.

D. W. Whitman 2008. The significance of body size in the Orthoptera: a review. Journal of Orthoptera Research 17:117–134. Google Scholar

251.

D. W. Whitman and L. J. Orsak . 1985. Biology of Taeniopoda eques (Orthoptera: Acrididae) in southeastern Arizona. Annals Entomological Society of America 78:811–825. Google Scholar

252.

D. W. Whitman, M. S. Blum, and C. G. Jones . 1985. Chemical defense in Taeniopoda eques (Orthoptera: Acrididae): role of the metathoracic secretion. Annals Entomological Society of America 78:451–455. Google Scholar

253.

D. W. Whitman, M. S. Blum, and C. G. Jones . 1986. Olfactorily mediated attack suppression in the southern grasshopper mouse toward an unpalatable prey. Behavioural Processes 13:77–83. Google Scholar

254.

D. W. Whitman, M. S. Blum, and D. W. Alsop . 1990. Allomones: chemicals for Defense. pp 289–351. In D. Evans and J. Schmidt , editors. (Eds). Arthropod Defenses Adaptive Mechanisms and Strategies of Prey and Predators. State University of New York Press. Albany, New York. Google Scholar

255.

D. W. Whitman, J. P. Billen, D. Alsop, and M. S. Blum . 1991. Anatomy, ultrastructure, and functional morphology of the metathoracic tracheal defensive glands of the grasshopper Romalea guttata. Canadian Journal of Zoology 69:2100–2108. Google Scholar

256.

D. W. Whitman, C. G. Jones, and M. S. Blum . 1992. Defensive secretion production in lubber grasshoppers (Orthoptera:Romaleidae): influence of age, sex, diet, and discharge frequency. Annals Entomological Society of America 85:96–102. Google Scholar

257.

D. S. Wilson 1975. The adequacy of body size as a niche difference. American Naturalist 109:769–784. Google Scholar

258.

I. J. Winfield and C. R. Townsend . 1983. The cost of copepod reproduction: increased susceptibility to fish predation. Oecologia 60:406–411. Google Scholar

259.

G. Woodward, D. C. Speirs, and A. G. Hildrew . 2005. Quantification and resolution of a complex, size-structured food web. Advances in Ecological Research 36:85–135. Google Scholar

260.

R. Yosef and D. W. Whitman . 1992. Predator exaptations and defensive adaptations in evolutionary balance: no defense is perfect. Evolutionary Ecology 6:527–536. Google Scholar

Notes

[1] 1We will refer to R. microptera and T. eques as “lubbers,” although that term is often applied to all members of the family Romaleidae.

[2] 2To understand lubber defense ecology, we tested lubbers against 112 species of various predator taxa. Given the two separate defense mechanisms and the great physiological, morphological, and behavioral diversity among grasshopper predators, it is not surprising that we observed virtually every type of predator response against lubbers. The results of these trials will be published elsewhere.

[3] 3In a different study, we observed loggerhead shrikes, Lanius ludovicians, capture R. microptera grasshoppers and impale them on barbwire fences, possibly as a sexual or territorial display. We did not observe consumption of the fresh-caught grasshoppers (Yosef & Whitman 1992).

[4] 4We tabulated “body length” from various sources. However, different authors recorded body length in different ways (i.e., fastigium to tip of abdomen vs fastigium to tip of hind femora vs fastigium to wing tip), and it is not always clear which method they used. Most measurements are probably based on dried museum specimens, which are shorter than live specimens. In addition, grasshopper masses and lengths vary widely geographically, annually, seasonally, with local environmental conditions, and in females, during the gonotrophic cycle. Also, nomenclature changes over time, and the taxonomic designation for many of the early descriptions for size or chemical defense are questionable. Hence, our data can only be considered as the best current estimate of the situation.

Douglas W. Whitman and Shawn Vincent "Large size as an antipredator defense in an insect," Journal of Orthoptera Research 17(2), 353-371, (1 December 2008). https://doi.org/10.1665/1082-6467-17.2.353
Accepted: 1 December 2008; Published: 1 December 2008
KEYWORDS
Acrididae
allomone
Antipredator defense
body size
chemical defense
defense mechanism
grasshopper
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