PHYSIOLOGICAL ECOLOGY Does Dietary P Affect Feeding and Performance in the Mixed-Feeding Grasshopper (Acrididae) Melanoplus bivitattus? VIVIANA LOAIZA, JAYNE L. JONAS, AND ANTHONY JOERN1 Division of Biology, Kansas State University, Manhattan, KS 66506 Environ. Entomol. 37(2): 333Ð339 (2008) ABSTRACT Although consequences of limited dietary protein and carbohydrate to performance are well studied for terrestrial insect herbivores, the importance of phosphorus (P) remains poorly understood. We examined the signiÞcance of dietary P to performance in Þfth-instar nymphs of the grasshopper Melanoplus bivittatus fed artiÞcial diets. Consumption, digestion, developmental rate, and growth in response to different levels of P nested within standard-Protein and carbohydrate diets were determined. Developmental rate was slowest on high-P diets; protein:carbohydrate concentration and P in diets affected frass production and consumption. Approximate digestibility and conversion of digested food were primarily inßuenced by the protein:carbohydrate quality of the diet but not P. Mass gain was marginally lower in the low-Protein:high carbohydrate diet used in this study. At the individual level, other than small effects to developmental rate at high concentrations for M. bivittatus, dietary P otherwise seems to have little effect on nymphal performance. To the degree that it is important, effects of dietary P depend on the concentrations of protein and carbohydrate in the diet. KEY WORDS dietary phosphorus limitation to grasshoppers, ecological stoichiometry, nutritional ecology, multiple nutrients, nutritional indices A large mismatch exists between the elemental stoichiometry of herbivore tissues and that of their host plants (McNeil and Southwood 1978, Mattson 1980, Bernays 1982, Denno and McClure 1983, Strong et al. 1984, Elser et al. 2000a,b). For example, concentrations of nitrogen (N) and phosphorus (P) in plants may be as much as 10 Ð20 times lower in plant tissues than that observed in herbivore tissues. Despite the imbalance between nutritional and physiological needs, homeostatic mechanisms maintain concentrations of herbivore tissues within narrow limits (Slansky and Feeny 1977, Slansky and Scriber 1985, Abisgold and Simpson 1987, Yang and Joern 1994), indicating the need to understand the regulation of limiting nutrients (Sterner and Elser 2003). For insect herbivores, protein and carbohydrate have been shown repeatedly to limit through performance penalties if a key nutrient is in short supply (McNeil and Southwood 1978, Mattson 1980, White 1993, Joern and Behmer 1998) or if diets are not balanced (Simpson and Raubenheimer 1993, Raubenheimer and Simpson 1997). A small number of recent studies now document that dietary P may also play a greater limiting role in terrestrial herbivores than was previously expected (Elser et al. 2000a,b; Schade et al. 2003; Perkins et al. 2004), a conclusion recognized for some time for aquatic herbivores (Elser et al. 1988, Elser and Urabe 1999, Sterner and Elser 2003). 1 Corresponding author, e-mail: [email protected]. The imbalance in stoichiometric relationships of carbon (C), N, and P in herbivore tissues compared with their food potentially inßuences individual performance (Sterner and Elser 2003), population and community dynamics (Fagan et al. 2002, Andersen et al. 2004, Fagan and Denno 2004, Hall 2004, Raubenheimer and Simpson 2004), and nutrient cycling (Elser and Urabe 1999, Sterner and Elser 2003, Elser 2006). Intriguing phylogenetic, trophic, and size relationships between the elemental composition of consumers and food have also been identiÞed (Elser et al. 2000a, Fagan et al. 2002, Woods et al. 2004, Kerkhoff et al. 2006). Although many signiÞcant physiological, ecological, and evolutionary relationships have been described for aquatic taxa in response to dietary P (Elser et al. 2000a, Sterner and Elser 2003), terrestrial species are not well studied, including the issue of whether P is limiting to terrestrial insect herbivores (Schade et al. 2003, Perkins et al. 2004, Woods et al. 2004). Substantial syntheses based on Þrst principles predict that dietary P limits consumers (Elser et al. 1996). As one example, the growth rate hypothesis (Elser et al. 1996) predicts that rapid growth rate requires high investment in ribosomes needed for protein synthesis. Ribosomes contain a large fraction of cellular RNA and are particularly rich in P (⬇10% of organismal mass and most organismal P is found in ribosomes) (Elser et al. 2000b, Sterner and Elser 2003, Woods et al. 2003). Dietary P could easily become limiting in 0046-225X/08/0333Ð0339$04.00/0 䉷 2008 Entomological Society of America 334 ENVIRONMENTAL ENTOMOLOGY Table 1. Vol. 37, no. 2 Elemental composition of artificial diets used in experiments to cross P concentration with that of protein and carbohydrate Percent protein:percent carbohydrate Phosphorus level %C %N %P C:N C:P N:P 14:28 14:28 14:28 21:21 21:21 21:21 28:14 28:14 28:14 Low Standard High Low Standard High Low Standard High 41.93 41.93 39.70 42.96 42.96 40.73 43.99 43.99 41.77 1.91 1.91 1.91 2.86 2.86 2.86 3.81 3.81 3.81 0.34 0.58 1.74 0.50 0.75 1.90 0.67 0.91 2.07 21.95 21.95 20.8 15.0 15.0 14.2 11.5 11.5 10.96 123.3 72.3 22.8 85.9 85.9 21.4 65.7 48.3 20.2 5.62 3.3 1.1 5.72 3.8 1.50 5.67 4.2 1.84 Protein:carbohydrate diets are in standard use (Simpson and Raubenheimer 2001, Behmer et al. 2002), and P was modiÞed according to Perkins et al. (2004). Percentages of elements in diets were determined from stoichiometric calculations of ingredients in diet recipes. Phosphorus concentrations diets averaged 0.5% for low, 0.75% for standard, and 1.9% for high levels. taxa with rapid growth rates. Moreover, compared with N (Fagan et al. 2002), which varies considerably among insect taxa, the potential for P limitation in insects seems to be universal. P levels do not differ systematically between herbivores and predators, and only a weak phylogenetic signal at the ordinal level is observed (Woods et al. 2004). A general inverse relationship between P content and body size exists in many insect groups, but it is only marginally signiÞcant for Orthoptera (Woods et al. 2004). In this study, we examined possible P limitation to nymphs of the grasshopper Melanoplus bivittatus (Say) during the Þfth instar. Mineral limitation from N in grasshoppers is well known (Hinks et al. 1993, White 1993, Joern and Behmer 1997, 1998), and extensive state-space analyses of the combined effects of protein and carbohydrate on grasshopper performance indicate a dynamic interaction among primary nutrients (Raubenheimer 1992, Simpson and Raubenheimer 1993, 2000, Behmer et al. 2001, 2002). Knowledge of such relationships provides an ideal background against which to assess the impact of P because it allows us to assess interactions among nutrients. Rapidly growing individuals such as prereproductive grasshopper nymphs must accumulate a signiÞcant amount of new tissues over a short period of time. Such growth requires a large investment in N-rich proteins and P-rich rRNA, which constitute large portions of individual N and P budgets, respectively (Elser et al. 1996, 2000a). Using artiÞcial standard diets for grasshoppers (Abisgold and Simpson 1987, Simpson and Raubenheimer 1993) modiÞed according to Perkins et al. (2004), we test two hypotheses: (1) that dietary P limits nymphal grasshopper performance in the form of growth and development and (2) that consumption and postingestive regulation of food is inßuenced by dietary P levels. Feeding and performance by the mixed-feeding grasshopper M. bivittatus is assessed on different diets in which dietary P concentrations are varied against a background of diets with protein:carbohydrate (p:c) ratios known to be near optimal (21%p:21%c; Behmer and Joern 2008). Materials and Methods Study Organism. Melanoplus bivittatus (Orthoptera: Acrididae) is a large polyphagous grasshopper species common in grasslands throughout much of North America, which feeds on both forbs and grasses (Mulkern et al. 1969, Capinera et al. 2004). Nymphs develop in midsummer during the period that foliar nutritional quality is undergoing its greatest change, and grasshoppers generally encounter highly variable food in the Þeld (Joern and Mole 2005). Feeding Trials. Diet consumption and performance by Þfth-instar nymphs of M. bivittatus was evaluated using controlled diets that varied in the percentage of protein (p), carbohydrate (c), and phosphorus (P). After completing egg diapause, nymphs hatched from eggs of Þeld-caught adults were reared in an insectary maintained at 30⬚C on a 14:10 light:dark photophase. Incandescent lamps (40 W) placed near cages provided light and heat. Before use in experiments, nymphs were fed unlimited seedling wheat, romaine lettuce, and wheat bran mixed with brewerÕs yeast. Within 12 h of molting to the Þfth instar, nymphs were weighed, transferred into individual cages, and provided with a randomly assigned diet. Feeding Experiments. Feeding trials were performed as a 3 ⫻ 3 factorial experiment (p:c diet type ⫻ dietary-P level) arranged in a completely randomized design (Steel and Torrie 1980). Nine dry, granular, chemically deÞned diets were prepared in a manner similar to those described previously (Simpson and Raubenheimer 1993, Behmer et al. 2001). We varied protein and digestible carbohydrates to provide three p:c combinations (all values are expressed on a percentage dry mass basis): (1) p14:c28, (2) p21:c21, and (3) p28:c14. All foods had equal amounts of digestible macronutrients (protein plus carbohydrate equaled 42% as a proportion of total dry mass, an amount typical for plant material) and were identical in the amounts of the other ingredients, including indigestible cellulose powder. The P level of artiÞcial diets was modiÞed from this standard grasshopper diet (Simpson and Raubenheimer 1993) following Perkins et al. (2004) and nested as three levels within each p:c diet (Table 1). Low-P diets were prepared by withholding April 2008 LOAIZA ET AL.: PHOSPHORUS LIMITATION the major sources of P (phosphoric acid, iron phosphate, and calcium phosphate) contained in the WessonÕs salts mixtures and raised in the high-P diets by adding dibasic sodium phosphate, following the approach of Perkins et al. (2004). The standard-P diet is the P concentration in the standard grasshopper diet. P levels in the diets averaged 0.5, 0.75, and 1.9% percent for low, standard, and high levels, respectively. Other major sources of P in the diet were casein and albumin and were not varied. A standard feeding protocol was followed (Behmer et al. 2001). Diets were assigned to arenas in a completely randomized design with 10 replicates of each diet. Food was placed into food dishes and stored in a drying cabinet at 32⬚C for 24 h before weighing. After weighing to the nearest 0.1 mg, foods were placed inside the arenas, and grasshoppers were allowed to feed for 72 h, after which the food dish was removed and replaced with a fresh, preweighed dish of food. The food dish that was removed was placed in the drying cabinet for 24 h before being reweighed. This procedure was repeated until the grasshopper either molted or died. Data Analyses. The initial and Þnal insect wet weights, Þnal insect dry weight, days until Þnal molt, frass dry weight, and amount of diet consumed were measured for each grasshopper. Initial dry weight was estimated by regressing dry and fresh weights of nymphs at the beginning of the study (n ⫽ 14, dry mass ⫽ 0.033 ⫹ 0.125 ⫻ wet mass, R2 ⫽ 0.474). Nymphs that died before the Þnal molt were not included in subsequent analyses. We examined the effect of diet over the entire Þfth instar for the following dependent variables: consumption, frass production, mass gained, developmental rate (time to complete Þfth instar), relative growth rate, and estimates of food use efÞciency (commonly referred to as approximate digestibility, efÞciency of conversion of ingested food, and efÞciency of conversion of digested food). Relative growth rate (RGR) was calculated as [(ln Þnal weight ⫺ ln initial weight)/days] (Hunt 1978). Two-way analysis of variance (ANOVA) tests and Fisher least signiÞcant difference (lsmeans) were used for post hoc analysis of pairwise comparisons for signiÞcant effects in SAS (v.9.1; SAS Institute, Cary, NC). Only statistically signiÞcant relationships are presented in the results section except that we indicate when the effect of P is marginally signiÞcant to be conservative about evaluating its importance. Variables were transformed to satisfy normality assumptions, and the variances of all transformed variables were homogenous. Time elapsed (days) to complete the Þfth instar was transformed into developmental rate using the inverse of the square root. Approximate digestibility (AD), efÞciency of conversion of digested food (ECD), and efÞciency of conversion of ingested food (ECI) were calculated according to Waldbauer (1968). To account for ratios, analysis of covariance (ANCOVA) was used (Raubenheimer and Simpson 1992, Horton and Redak 1993) to analyze consumption and frass production (each with initial 335 dry body mass as the covariate), AD (amount of food assimilated with food consumed as the covariate), ECI (mass gained with consumption as the covariate), and ECD (mass gained with food digested as the covariate). Results Feeding Trials. Over the Þfth-instar stadium in M. bivittatus, consumption and conversion of digested food (ECD) were primarily inßuenced by the p:c ratio of the diet. Dietary P inßuenced developmental rates, whereas weight gain and RGR were not affected by the diets used in this study. An interaction between p:c ratio and P was observed for frass production and AD. Survival. Average survival of Þfth-instar nymphs was 83% and was not inßuenced by either p:c ratio (2 ⫽ 0.00, P ⫽ 1.00) or P concentration (2 ⫽ 0.8, P ⫽ 0.96) of the diets. Consumption. The p:c ratio in the diet inßuenced the amount consumed over the Þfth instar (Fig. 1a; Table 2). Initial dry weight was a signiÞcant covariate. SigniÞcantly more of the p21:c21 diet was consumed than either the p14:c28 or p28:c14 diets. P level had a marginally signiÞcant negative effect on consumption, but there was no interaction between the p:c diet and P. Food Processing and Digestibility. Both dietary p:c ratio and P affected frass production over the Þfth instar (Fig. 1b; Table 2). Initial mass was a signiÞcant covariate. Individuals fed p14:c28 diets produced signiÞcantly less frass than those fed the p21:c21 or p28: c14 diets (Fig. 1b; t ⫽ 2.62, P ⬍ 0.01 and t ⫽ 2.04, P ⬍ 0.05, respectively). The high dietary P diet produced less frass than either the low and standard levels (t ⫽ 2.12, P ⬍ 0.04 and t ⫽ 2.12, P ⬍ 0.04, respectively), which were not different from one another. AD was signiÞcantly affected by p:c, whereas there was a marginally signiÞcant interaction between p:c and P (Fig. 1c; Table 2). The amount consumed was highly signiÞcant as a covariate. As a pattern, AD generally decreases as protein levels in the diet increase. The p28:c14 diet is signiÞcantly different than the p21:c21 diet and the p14:c28 diet. ECD varied signiÞcantly with dietary p:c ratio (Fig. 1d; Table 2). The covariate was highly significant. ECD generally increased for diets with higher protein. Individuals were more efÞcient at digesting p28:c14 than p14:c28 diets and marginally more efÞcient than the p21:c21 ratio. No signiÞcant effect was observed in ECI. Developmental Rate. Dietary P signiÞcantly affected developmental rate (Fig. 2a; Table 2), measured as the number of days required to complete the Þfth-instar stadium. More time was required to complete development on the high-P treatment compared with the standard and low-P levels. Weight Gain. No signiÞcant effects of diet on total weight gain or RGR were observed (Table 2). If there was any effect of diet, p:c ratio had perhaps the greatest inßuence on total weight gain (P ⫽ 0.088), with 336 ENVIRONMENTAL ENTOMOLOGY Vol. 37, no. 2 Fig. 1. Consumption and whole individual digestion by Þfth-instar M. bivitattus in response to crossed combinations of standard diets that vary in ratios of percent protein:percent carbohydrate as indicated with three levels of dietary P labeled as L (low), S (standard), and H (high). Effect of dietary P is shown only if results are signiÞcant or near signiÞcant. The following responses to diet combinations are presented: (a) dry mass of food consumed (mean, SE), (b) frass production (mean, SE), (c) approximate digestibility (AD; mean, SE), and (d) efÞciency of conversion of digested food (mean, SE). nymphs fed the p21:c21 diets gaining more weight than those fed the p14:c28 diet (Fig. 2b). Discussion Determining which combinations of minerals or nutrients limit insect herbivores is a major challenge in nutritional ecology, especially given the large number of possible combinations (Clancy and King 1993) and the structural barriers to extracting nutrients (Clissold et al. 2006) that may be involved. Here we studied the problem of whether dietary P limits performance in a developing insect herbivore when combined with diets that differ in combinations of protein and carbohydrate. This scenario of variable diets is representative of daily challenges faced by free-ranging individuals in natural environments. In the Þeld, grasshoppers routinely encounter food that is highly variable in nutrient content, making it unlikely that an optimal diet is readily attained by eating a single host species. Mixed-feeders such as M. bivittatus meet this challenge in part by feeding on a variety of different food plants (Bernays and Raubenheimer 1991), which may permit them to balance nutrient intake. Because the nutritional background of potential food under natural conditions is so variable, it is appropriate to assess the contribution of a single portion of the diet against multiple diets. We do this by comparing performance by nymphs on a range of diets in which concentrations and relative abundances of nutrients are within the range of those observed in naturally occurring plants (Agren 2004, Kerkhoff et al. 2006). Moreover, these diets bracket levels of p:c ratios known to best support performance of this species (Behmer and Joern 2008). Our results indicate that dietary P can be marginally important to M. bivittatus, but our overall impression of its signiÞcance suggests it is best understood with respect to other components of the diet (p:c ratios in this study) and not as the contribution of a single mineral nutrient acting independently (Clissold et al. 2006). Also, p:c ratio treatments were generally more signiÞcant than P. Because no-choice diets were used in these experiments, grasshoppers were not able to mix foods to balance nutrient demands, although other studies indicate that M. bivittatus does balance the p:c ratio in the diet when given a choice (Jonas 2007). This study examines three components of the problem: consumption, digestion (processing and conversion of diet), and the eventual performance of the individuals (growth, developmental rate, or survival). A major conclusion from this study is that the grasshoppers regulated nutritional needs through combined consumption and digestion, with the result that performance is not greatly impacted by variable diets. However, we cannot determine directly whether elemental regulation occurred because N or P use efÞciencies were not measured in this study. As described above, an ecological stoichiometric framework predicts that both N and P can potentially limit insect herbivores, but P is less well studied in terrestrial systems. In rapidly growing individuals, Prich rRNA may be at a premium, leading to the Plimited growth rate hypothesis (Elser et al. 1996), which predicts that increased levels of P in the diet (to a point) should support increased growth rate. For example, elevated dietary P levels increased growth and shortened developmental time in larval Manduca sexta (Perkins et al. 2004). For M. bivittatus in this study, P levels did not signiÞcantly inßuence either April 2008 LOAIZA ET AL.: PHOSPHORUS LIMITATION 337 Table 2. ANOVA and ANCOVA summary of significant responses in feeding, digestion, and performance by M. bivittatus to protein:carbohydrate and P diet combinations Dependent variable Consumption Model p:c P p:c ⫻ P Initial dry weight (g) Error Frass production p:c P p:c ⫻ P Initial dry weight (g) Error AD p:c P p:c ⫻ P Amount consumed (g) Error ECI p:c P p:c ⫻ P Amount consumed (g) Error ECD p:c P p:c ⫻ P Food assimilated (g) Error Developmental p:c rate P p:c ⫻ P Error Total weight p:c gain (g) P p:c ⫻ P Error RGR p:c P p:c ⫻ P Error df Mean square F 2 2 4 1 0.11878 0.08582 0.03223 0.29972 3.32 2.40 0.90 8.38 62 2 2 4 1 0.03578 0.03803 0.03008 0.01404 0.18164 65 2 2 4 1 0.01012 0.03699 12.86 ⬍0.0001 0.00320 1.11 0.335 0.00671 2.33 0.065 0.61906 215.27 ⬍0.0001 62 2 2 4 1 0.00288 0.00088 0.00078 0.00166 0.02717 1.01 0.370 0.89 0.414 1.90 0.122 31.18 ⬍0.0001 62 2 2 4 1 0.00087 0.00331 0.00145 0.00193 0.01560 3.12 1.37 1.83 14.74 0.051 0.262 0.135 0.0003 62 2 2 4 66 2 2 4 66 2 2 4 65 0.00106 0.00043 0.00607 0.00171 0.00088 0.00630 0.00325 0.00513 0.08239 0.00345 0.00197 0.00113 0.00142 0.49 6.88 0.11 0.617 0.002 0.114 2.52 1.30 1.03 0.088 0.279 0.400 2.43 1.39 0.80 0.096 0.258 0.533 P 0.043 0.099 0.469 0.005 3.76 0.029 2.97 0.058 1.39 0.248 17.94 ⬍0.0001 Only responses that are signiÞcant (P ⬍ 0.05) or nearly signiÞcant (0.05 ⱕ P ⬍ 0.1) are shown. Covariates are omitted if they are not signiÞcant. total weight gain or relative growth rate. In the p14:c28 and p21:c21 diets, however, there was a tendency for the individuals fed the standard-P diet (1% P) to gain more than those fed the low-P or high-P diets (Fig. 2b). Counter to the Þndings of Perkins et al. (2004), we found that individuals fed the low-P and standard-P diets developed signiÞcantly faster than those fed the high-P diets. In our experiments, P levels in diets ranged from 0.34% at the lowest level to 1.90% at the highest. The P concentration in the high-P diets was greater than that observed in most plant tissues (Kerkhoff et al. 2006). If herbivores are homeostatic for speciÞc nutrient levels or ratios, it may be costly if one mineral nutrient is considerably out of balance from others because consumers incur a “metabolic handling cost” resulting in lowered performance; this response was also predicted for p:c comparisons in the geometric Fig. 2. Performance by Þfth-instar M. bivittatus in response to diet combinations. Responses include (a) developmental rate measured as the number of days until the Þfth-instar individual molt to adults (mean, SE) and (b) growth expressed as dry mass gained (mean, SE). model of Simpson and Raubenheimer (2000). For example, such a cost is implicated for a variety of consumers where growth rates peaked at P- levels of ⬇1% of dry mass and decreased at higher P concentrations in diet (Boersma and Elser 2006). Ultimately, a multivariate framework for understanding nutritional needs of herbivores is needed where performance reßects ratios of nutrients, not just the action of individual elements (Simpson and Raubenheimer 2000, 2001). Evidence for the importance of this approach was shown in our study, but a more reÞned analysis of digestion is needed to quantify such costs to an unbalanced diet. Discussion continues about how to best understand nutrient limitation, either as complex macronutrients and dietary ratios, individual elements or their ratios, or some combination of the two. Our results add to the small but increasing number of examples indicating the potential importance of P within the context of p:c ratios for performance in immature terrestrial insect herbivores. We show that the mineral nutrient P affects developmental rate in growing nymphs of a common grasshopper, M. bivittatus but that nutrient acquisition is regulated to minimize affects of dietary P on performance on diets with near optimal protein: carbohydrate ratios. Ecological stoichiometry has focused primarily on elemental responses, in part because of research interest in nutrient cycling motivating the development of the Þeld (Elser and Urabe 1999, Sterner and Elser 2003), capability of speciÞc elements to act as a useful proxy for complex nutritional limitation, and the development of compelling explanations across organizational scales based on elements (Elser et al. 1996). The element-biased view contrasts with equally compelling physiological argu- 338 ENVIRONMENTAL ENTOMOLOGY ments that require an understanding of how elements interact as nutrients (e.g., protein, carbohydrate, lipids) to understand the context in which elements become limiting (Simpson and Raubenheimer 2001). Our study with P indicates that, at a minimum, a multiple resource-ratio approach is needed to understand individual elements (Clissold et al. 2006). Only small effects of dietary P were detected compared with other components of the diet, indicating that more effort to understand the importance of P for terrestrial insect herbivores is needed. How do stoichiometric approaches to explain performance Þt with other ecological factors also affecting foraging and the resulting nutritional consequences by insect herbivores? Because inßuences of feeding and nutrition in natural systems are multifactorial (Pitt 1999, Danner and Joern 2004), nutrient limitation often emerges even when food is seemingly abundant and of sufÞcient nutritional quality. Reduced time available for searching and consuming optimal diets is common for many reasons. Abiotic conditions are often unsuitable, nonoptimal spatial arrangement of complementary nutritional resources limit diet mixing within the time frame available for foraging, or the effects of predators on feeding behavior may prevent insect herbivores from optimally exploiting food resources. Each of these factors makes Þnding quality, balanced diets important. It may be difÞcult to balance a diet if less time is available for Þnding it (e.g., predation) or abiotic conditions are suboptimal for processing it (e.g., digestion). Acknowledgments Logistical support from Konza Prairie Biological Station and the KSU Grassland Ecology REU program is gratefully acknowledged. We thank J. Higgins (KSU Math and Statistics Department) for advice on the experimental design and S. Parsons for assistance with the laboratory feeding trials. Research was supported by NSF Grant DEB0456522 (to A.J.) and the NSF Konza Prairie LTER and KSU Prairie REU program (NSF Grant DBI0552930). J. Apple, S. Behmer, and A. Laws provided helpful comments on the manuscript. References Cited Abisgold, J. D., and S. J. Simpson. 1987. The physiology of compensation by locusts for changes in dietary protein. J. Exp. Biol. 129: 329Ð346. Agren, G. I. 2004. The C:N:P stoichiometry of autotrophsÑ theory and observations. Ecol. Lett. 7: 185Ð191. Andersen, T., J. F. Elser, and D. O. Hessen. 2004. Stoichiometry and population dynamics. Ecol. Lett. 7: 884Ð900. Behmer, S. T., and A. Joern. 2008. Coexisting generalist herbivores occupy unique nutritional feeding niches. Proc. Nat. Acad. Sci. (USA) 105: 1977Ð1982. Behmer, S. T., D. Raubenheimer, and S. J. Simpson. 2001. Frequency-dependent food selection in locusts: a geometric analysis of the role of nutrient balancing. Anim. Behav. 61: 995Ð1005. Behmer, S. T., S. J. Simpson, and D. Raubenheimer. 2002. Herbivore foraging in chemically heterogeneous environments: nutrients and secondary metabolites. Ecology 83: 2489Ð2501. Vol. 37, no. 2 Bernays, E. A. 1982. The insect on the plantÑa closer look, pp. 3Ð17. In J. H. Visser and A. J. Minks (eds.), Proceedings of the 5th international symposium on insect-plant relationships. Pudoc, Wageningen, The Netherlands. Bernays, E. A., and D. Raubenheimer. 1991. Dietary mixing in grasshoppers: changes in acceptability of different secondary compounds associated with low levels of dietary proteins. J. Insect Behav. 4: 545Ð556. Boersma, K., and J. F. Elser. 2006. Too much of a good thing: on stoichiometrically balanced diets and maximal growth. Ecology 87: 1325Ð1330. Capinera, J. L., R. D. Scott, and T. J. Walker. 2004. Field guide to grasshoppers, katydids, and crickets of the United States. Cornell University Press, Ithaca, NY. Clancy, K. M., and R. M. King. 1993. DeÞning the western spruce budwormÕs nutritional niche with response surface methodology. Ecology 74: 442Ð 454. Clissold, F. J., G. D. Sanson, and J. Read. 2006. The paradoxical effects of nutrient ratios and supply rates on an outbreaking insect herbivore, the Australian plague locust. J. Anim. Ecol. 75: 1000 Ð1013. Danner, B. J., and A. Joern. 2004. Development, growth and egg production of the common grasshopper, Ageneotettix deorum (Orthoptera: Acrididae) in response to indirect risk of spider predation. Ecol. Entomol. 29: 1Ð11. Denno, R. F., and M. S. McClure [eds.]. 1983. Variable plants and herbivores in natural and managed systems. Academic, New York. Elser, J. F. 2006. Biological stoichiometry: a chemical bridge between ecosystem ecology and evolutionary biology. Am. Nat. 168(Suppl.): S25ÐS35. Elser, J. J., and J. Urabe. 1999. The stoichiometry of consumer-driven nutrient recycling: theory, observations, and consequences. Ecology 80: 745Ð751. Elser, J. J., D. R. Dobberfuhl, N. A. MacKay, and J. H. Schampel. 1996. Organism size, life history, and N:P stoichiometry: towards a uniÞed view of cellular and ecosystem processes. BioScience 46: 674 Ð 684. Elser, J. J., W. F. Fagan, R. F. Denno, D. R. Dobberfuhl, A. Folarin, A. Huberty, S. Interlandi, S. S. Kilham, E. McCauley, K. L. Schulz, E. H. Siemann, and R. W. Sterner. 2000a. Nutritional constraints in terrestrial and freshwater food webs. Nature (Lond.) 408: 578 Ð580. Elser, J. J., R. W. Sterner, E. Gorokhova, W. F. Fagan, T. A. Markow, J. B. Cotner, J. F. Harrison, S. E. Hobbie, G. M. Odell, and L. J. Weider. 2000b. Biological stoichiometry from genes to ecosystems. Ecol. Lett. 3: 540 Ð550. Elser, J. J., M. M. Elser, N. A. Mackay, and S. R. Carpenter. 1988. Zooplankton-mediated transitions between N- and P-limited algal growth. Limnol. Oceanograph. 33: 1Ð14. Fagan, W. F., and R. F. Denno. 2004. Stoichiometry of actual vs. potential predator-prey interactions: insights into nitrogen limitation for arthropod predators. Ecol. Lett. 7: 876 Ð 883. Fagan, W. F., E. H. Siemann, C. Mitter, R. F. Denno, A. Huberty, H. A. Woods, and J. F. Elser. 2002. Nitrogen in insects: implications for trophic complexity and species diversiÞcation. Am. Nat. 160: 784 Ð 802. Hall, S. R. 2004. Stoichiometrically explicit competition between grazers: species replacement, coexistence, and priority effects along resource supply gradients. Am. Nat. 164: 157Ð172. Hinks, C. F., D. Hupka, and O. Olfert. 1993. Nutrition and the protein economy in grasshoppers and locusts. Comp. Biochem. Physiol. 104: 133Ð142. Horton, D. R., and R. A. Redak. 1993. Further comments on analysis of covariance in insect dietary studies. Entomol. Exp. Appl. 69: 263Ð275. April 2008 LOAIZA ET AL.: PHOSPHORUS LIMITATION Hunt, R. 1978. Plant growth analysis. Edward Arnold Publishers, Southampton, United Kingdom. Joern, A., and S. T. Behmer. 1997. Importance of dietary nitrogen and carbohydrates to survival, growth and reproduction in adult Ageneotettix deorum (Orthoptera: Acrididae). Oecologia (Berl.) 112: 201Ð208. Joern, A., and S. T. Behmer. 1998. Impact of diet quality on demographic attributes in adult grasshoppers and the nitrogen limitation hypothesis. Ecol. Entomol. 23: 174 Ð 184. Joern, A., and S. Mole. 2005. The plant stress hypothesis and variable responses by blue grama grass (Bouteloua gracilis) to water, mineral nitrogen and insect herbivory. J. Chem. Ecol. 31: 2069 Ð2090. Jonas, J. L. 2007. Nutrient resources and stoichioometry affect the ecology of above- and belowground invertebrate consumers. Division of Biology, Kansas State University, Manhattan, KS. Kerkhoff, A. J., W. F. Fagan, J. F. Elser, and B. J. Enquist. 2006. Phylogenetic and growth form variation in the scaling of nitrogen and phosphorus in the seed plants. Am. Nat. 168: E103ÐE122. Mattson, W. J. 1980. Herbivory in relation to plant nitrogen content. Annu. Rev. Ecol. System. 11: 119 Ð161. McNeil, S., and T.R.E. Southwood. 1978. The role of nitrogen in the development of insect-plant relationships, pp. 77Ð98. In J. B. Harborne (ed.), Biochemical aspects of plant and animal coevolution. Academic, London, United Kingdom. Mulkern, G. B., K. P. Pruess, H. Knutson, A. F. Hagen, J. B. Campbell, and J. D. Lambley. 1969. Food habits and preferences of grassland grasshoppers of the North Central Great Plains. Agricultural Experiment Station, North Dakota State University, Fargo, ND. Perkins, M. C., H. A. Woods, J. F. Harrison, and J. F. Elser. 2004. Dietary phosphorus affects the growth of larval Manduca sexta. Arch. Insect Biochem. Physiol. 55: 153Ð 168. Pitt, W. C. 1999. Effects of multiple vertebrate predators on grasshopper habitat selection: trade-offs due to predation risk, foraging and thermoregulation. Evol. Ecol. 13: 499 Ð 515. Raubenheimer, D. 1992. Tannic acid, protein, and digestible carbohydrate: dietary imbalance and nutritional compensation in locusts. Ecology 73: 1012Ð1027. Raubenheimer, D., and S. J. Simpson. 1992. Analysis of covarianceÑan alternative to nutritional indexes. Entomol. Exp. Appl. 62: 221Ð231. 339 Raubenheimer, D., and S. J. Simpson. 1997. Integrative models of nutrient balancing: application to insects and vertebrates. Nutr. Res. Rev. 10: 151Ð179. Raubenheimer, D., and S. J. Simpson. 2004. Organismal stoichiometry: quantifying non-independence among food components. Ecology 85: 1203Ð1216. Schade, J. D., M. Kyle, S. E. Hobbie, W. F. Fagan, and J. F. Elser. 2003. Stoichiometric tracking of soil nutrients by a desert insect herbivore. Ecol. Lett. 6: 96 Ð101. Simpson, S. J., and D. Raubenheimer. 1993. A multi-level analysis of feeding behaviour: the geometry of nutritional decisions. Phil. Trans. R. Soc. Lond. B. 342: 381Ð 402. Simpson, S. J., and D. Raubenheimer. 2000. The hungry locust. Adv. Study Behav. 29: 1Ð 44. Simpson, S. J., and D. Raubenheimer. 2001. The geometric analysis of nutrient-alleleochemical interactions: a case study using locusts. Ecology 82: 422Ð 439. Slansky, F., and P. P. Feeny. 1977. Stabilization of the rate of nitrogen accumulation by larvae of the cabbage butterßy on wild and cultivated plants. Ecol. Monogr. 47: 209 Ð228. Slansky, F., and J. M. Scriber. 1985. Food consumption and utilization, pp. 87Ð163. In G. A. Kurkut and L. I. Gilbert (eds.), Comprehensive insect biochemistry, physiology and pharmacology. Pergamon, Oxford, United Kingdom. Steel, R.G.D., and J. H. Torrie. 1980. Principles and procedures of statistics: a biometrical approach. McGraw-Hill, New York. Sterner, R. W., and J. F. Elser. 2003. Ecological stoichiometry: the biology of elements from molecules to the biosphere. Princeton University Press, Princeton, NJ. Strong, D. R., J. H. Lawton, and T.R.E. Southwood. 1984. Insects on plants: community patterns and mechanisms. Harvard University Press, Cambridge, MA. Waldbauer, G. 1968. The consumption and utilization of food by insects. Adv. Insect Physiol. 5: 229 Ð288. White, T.C.R. 1993. The inadequate environment: nitrogen and the abundance of animals. Springer, Berlin, Germany. Woods, H. A., W. Makino, J. B. Cotner, S. E. Hobbie, J. F. Harrison, K. Acharya, and J. J. Elser. 2003. Temperature and the chemical composition of poikilothermic organisms. Funct. Ecol. 17: 237Ð245. Woods, H. A., W. F. Fagan, J. F. Elser, and J. F. Harrison. 2004. Allometric and phylogenetic variation in insect phosphorus content. Funct. Ecol. 18: 103Ð109. Yang, Y., and A. Joern. 1994. Compensatory feeding in response to variable food quality by Melanoplus differentialis. Physiol. Entomol. 19: 75Ð 82. Received 12 March 2007; accepted 20 December 2007.
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