Why is maximal insect body size relatively small compared to that of vertebrates? Possibly insect body size is limited by the capacity of the tracheal respiratory system to delivery oxygen down longer and longer tracheae to the tissues. If so, one possible outcome would be that larger insect species would have a smaller safety margin for oxygen delivery (higher critical PO2, Pc). We tested this idea by exposing inactive adult grasshoppers of a range of species and body sizes(0.07–6.4 g) to progressively lower oxygen atmospheres and measuring their ventilation frequency and their ability to maintain metabolic rate(indexed by CO2 emission rate). We analyzed effects of body size on these parameters by simple linear regressions, as well as methods to control for phylogenetic relatedness among species. We found interspecific variation in Pc, but Pc did not significantly correlate with body mass (average Pc across all species =4 kPa). Maximal tracheal system conductance scaled approximately with mass0.7, and estimated ventilation in hypoxia (ventilatory frequency×tidal volume) scaled directly with mass, suggesting that convection is the major mechanism of gas exchange in all these species. These comparative data strengthen the growing body of evidence that body size does not affect the safety margin for oxygen delivery in insects.
Introduction
Why are the largest insects relatively small compared to vertebrates? Many explanations have been proposed. Some have argued that the exoskeleton would collapse if insects grew much larger; the larger size of aquatic than terrestrial invertebrates supports this hypothesis(Currey, 1967; Price, 1997). Possibly the vulnerability of insects during molting, combined with the enhanced benefit of larger prey to predators leads to size-dependent natural selection that reduces insect size (McGavin,2001). Perhaps the open circulatory system of insects cannot generate sufficient pressures to support fluid flow in very large insects; in support of this hypothesis, insects and spiders reach similar maximal sizes(about 100 g). Multiple authors have suggested that it is possible that the tracheal respiratory system cannot supply sufficient oxygen to sustain very large insects (Miller, 1966; Rutten, 1966; Tappan, 1974). In support of the latter idea, the appearance of gigantic insects in the fossil record coincides with the occurrence of high atmospheric PO2 levels (35%) (Berner and Landis,1988; Graham et al.,1995; Dudley,1998). Researchers have proposed that diffusive gas exchange was enhanced by these higher levels of O2, allowing insects to evolve larger body sizes (Miller,1966; Graham et al.,1995; Dudley,1998). One possible prediction of this hypothesis is that the safety margin for gas exchange should decrease with size across extant insect species, perhaps reaching zero in the largest species currently alive.
Safety margins for gas exchange can be measured by exposing insects to decreasing levels of O2 and recording the level at which metabolism can no longer be sustained (the critical PO2, Pc). Insects typically tolerate very low levels of O2 (<5%) (Greenlee and Harrison, 2004a), not only maintaining normal levels of O2 consumption and CO2 emission, but also being able to ventilate (Greenlee and Harrison,2004a), eat (Greenlee and Harrison, 2005), jump (Kirkton et al., 2005), and even fly(Chadwick and Williams, 1949; Joos et al., 1997) during substantial hypoxic exposures. However, to date it is unclear how the ability to function in hypoxia scales with body mass.
In insects, as with most other organisms, metabolic rates (and O2 consumption needs) change with body size, resulting from changes in tissue oxygen needs. Generally, as body size increases, absolute metabolic rate increases, while mass-specific metabolic rate decreases(Schmidt-Nielsen, 1984). Metabolic rate usually scales approximately with body mass to the power 0.75,with reported values ranging from 0.47 to 1.02(Peters, 1983). As insects increase in body size during development across instars, the safety margin for O2 delivery increases (grasshoppers)(Greenlee and Harrison, 2004a)or remains the same (caterpillars)(Greenlee and Harrison, 2005). However, it is possible that ontogenetic patterns in the safety margin for O2 delivery may be due to developmental changes such as the ability to respond to hypoxia rather than changes in body size per se(Greenlee and Harrison,2004a). To address this question, in this study we examined adults of grasshopper species differing in body size, challenging the respiratory system of each species with hypoxia to determine the Pc.
One possibility is that larger animals compensate for their increased body size (and increased gas exchange needs) by changing ventilatory parameters such as breathing frequency or tidal volume. In mammals and birds, breathing frequency scales with body mass to the –0.25 power, and tidal volume scales directly with mass, providing a scaling of pulmonary ventilation that matches the scaling of metabolic rate(Peters, 1983). The scaling of these ventilatory parameters has never been measured for insects. In addition,animals commonly respond to hypoxia with compensatory breathing (increasing ventilation frequency, tidal volume or both). In developing grasshoppers,ventilatory compensation for hypoxia (increasing frequency and tidal volume)increased with size across instars(Greenlee and Harrison,2004a). Again, it is possible that the observed pattern was merely due to development of the respiratory system as opposed to a compensatory mechanism in response to body size per se. To determine how ventilatory parameters scale with body size and to begin to investigate how the response to hypoxia varies with size in insects, we measured metabolic rates, tidal volumes and ventilatory frequencies in adults of grasshopper species across an order of magnitude range of body sizes while individuals were exposed to decreasing levels of atmospheric oxygen.
Materials and methods
Scaling and determination of Pc
Twenty-three species of grasshopper were collected throughout Arizona, USA. Animals were collected in 2001–2003 from the vicinities of Prescott Valley (112°25′W: 34°58′N), from Arivaca(111°33′W: 31°58′N) and from Yuma (114°67′W:33°25′N) (Table 1). We also include data from laboratory-reared Schistocerca americanaDrury for comparison. We transported animals back to the laboratory in screen cages with grass and forbs from their collection site. At the laboratory, up until the time of their experimental use, animals were kept at room temperature (25°C) with a light source provided for warmth during the day and given ad libitum access to green leaf lettuce and kale, in addition to their native plants. Animals were tested within 3 days of arrival at the laboratory. All animals were weighed to the nearest 0.001 g on a Mettler (Hightstown, NJ, USA) analytical balance prior to testing.
Family . | . | . | . | . | . |
---|---|---|---|---|---|
Subfamily . | . | . | . | . | . |
Tribe . | Genus species . | Abbreviation . | Collection site . | Collection date (month-year) . | Sample size . |
Romaleidae | |||||
Romaleinae | |||||
Romaleini | Brachystola magna | bm | Arivaca | 10-01*,† | 8 |
Taeniopoda eques | te | Arivaca | 10-01*,† | 8 | |
Acrididae | |||||
Melanoplinae | |||||
Dactylotini | Dactylotum variegatum | dv | Prescott Valley | 7-01* | 2 |
Hesperotettix viridis | hv | Prescott Valley | 6-01*,† | 1 | |
Hesperotettix viridis | hv | Prescott Valley | 7-01* | 4 | |
Poecilotettix sanguineus | ps | Prescott Valley | 6-01*,† | 10 | |
Melanoplini | Melanoplus aridus | ma | Arivaca | 9-03‡ | 1 |
Melanoplus differentialis | md | Arivaca | 10-01*,† | 8 | |
Melanoplus differentialis | md | Arivaca | 9-03‡ | 1 | |
Melanoplus femurrubrum | mf | Arivaca | 9-03‡ | 1 | |
Melanoplus gladstoni | mg | Arivaca | 9-03‡ | 1 | |
Melanoplus sanguinipes | ms | Prescott Valley | 6-01*,† | 14 | |
Melanoplus thomasi | mt | Arivaca | 9-03‡ | 1 | |
Melanoplus yarrowi | my | Arivaca | 9-03‡ | 1 | |
Cyrtacanthacridinae | |||||
Cyrtacanthacridini | Schistocerca americana | sca | Laboratory | *,† | 8 |
Schistocerca nitens | sn | Yuma | 9-03‡ | 1 | |
Gomphocerinae | |||||
Amblytropidiini | Syrbula admirabilis | sa | Arivaca | 7-02*,† | 8 |
Syrbula montezuma | sm | Arivaca | 7-02*,† | 8 | |
Boopedon nubilum | bn | Arivaca | 9-03‡ | 1 | |
Aulocarini | Ageneotettix deorum | ad | Prescott Valley | 7-01* | 1 |
Aulocara ellioti | ae | Prescott Valley | 6-01*,† | 7 | |
Psoloessa delicatula | pd | Prescott Valley | 7-01* | 4 | |
Psoloessa texana | pt | Arivaca | 7-02*,† | 4 | |
Cibolacrini | Heliaula rufa | hr | Prescott Valley | 7-01* | 6 |
Heliaula rufa | hr2 | Arivaca | 7-02*,† | 6 | |
Eritettigini | Amphitornus coloradus | ac | Prescott Valley | 6-01*,† | 7 |
Eritettix simplex | es | Prescott Valley | 6-01 and 7-01* | 5 | |
Opeia obscura | oo | Prescott Valley | 7-01* | 1 | |
Mermeriini | Mermiria bivitatta | mb | Arivaca | 9-03‡ | 1 |
Mermiria texana | met | Arivaca | 9-03‡ | 1 | |
no tribe | Acantherus piperatus | ap | Arivaca | 9-03‡ | 4 |
Parapomelini | Parapomala pallida | pp | Prescott Valley | 7-01* | 1 |
Parapomala pallida | pp | Arivaca | 9-03‡ | 3 | |
Oedipodinae | |||||
Hippiscini | Hadrotettix trifasciatus | ht | Prescott Valley | 7-01* | 4 |
Heliastus benjamini | hb | Arivaca | 9-03‡ | 1 | |
Leprus wheeleri | lw | Arivaca | 9-03‡ | 1 | |
Xanthippus corallipes | xc | Prescott Valley | 6-01*,† | 5 | |
Sphingonotini | Conozoa carinata | cc | Arivaca | 9-03‡ | 1 |
Trimerotropis pallidipennis | tp | Prescott Valley | 7-01* | 1 |
Family . | . | . | . | . | . |
---|---|---|---|---|---|
Subfamily . | . | . | . | . | . |
Tribe . | Genus species . | Abbreviation . | Collection site . | Collection date (month-year) . | Sample size . |
Romaleidae | |||||
Romaleinae | |||||
Romaleini | Brachystola magna | bm | Arivaca | 10-01*,† | 8 |
Taeniopoda eques | te | Arivaca | 10-01*,† | 8 | |
Acrididae | |||||
Melanoplinae | |||||
Dactylotini | Dactylotum variegatum | dv | Prescott Valley | 7-01* | 2 |
Hesperotettix viridis | hv | Prescott Valley | 6-01*,† | 1 | |
Hesperotettix viridis | hv | Prescott Valley | 7-01* | 4 | |
Poecilotettix sanguineus | ps | Prescott Valley | 6-01*,† | 10 | |
Melanoplini | Melanoplus aridus | ma | Arivaca | 9-03‡ | 1 |
Melanoplus differentialis | md | Arivaca | 10-01*,† | 8 | |
Melanoplus differentialis | md | Arivaca | 9-03‡ | 1 | |
Melanoplus femurrubrum | mf | Arivaca | 9-03‡ | 1 | |
Melanoplus gladstoni | mg | Arivaca | 9-03‡ | 1 | |
Melanoplus sanguinipes | ms | Prescott Valley | 6-01*,† | 14 | |
Melanoplus thomasi | mt | Arivaca | 9-03‡ | 1 | |
Melanoplus yarrowi | my | Arivaca | 9-03‡ | 1 | |
Cyrtacanthacridinae | |||||
Cyrtacanthacridini | Schistocerca americana | sca | Laboratory | *,† | 8 |
Schistocerca nitens | sn | Yuma | 9-03‡ | 1 | |
Gomphocerinae | |||||
Amblytropidiini | Syrbula admirabilis | sa | Arivaca | 7-02*,† | 8 |
Syrbula montezuma | sm | Arivaca | 7-02*,† | 8 | |
Boopedon nubilum | bn | Arivaca | 9-03‡ | 1 | |
Aulocarini | Ageneotettix deorum | ad | Prescott Valley | 7-01* | 1 |
Aulocara ellioti | ae | Prescott Valley | 6-01*,† | 7 | |
Psoloessa delicatula | pd | Prescott Valley | 7-01* | 4 | |
Psoloessa texana | pt | Arivaca | 7-02*,† | 4 | |
Cibolacrini | Heliaula rufa | hr | Prescott Valley | 7-01* | 6 |
Heliaula rufa | hr2 | Arivaca | 7-02*,† | 6 | |
Eritettigini | Amphitornus coloradus | ac | Prescott Valley | 6-01*,† | 7 |
Eritettix simplex | es | Prescott Valley | 6-01 and 7-01* | 5 | |
Opeia obscura | oo | Prescott Valley | 7-01* | 1 | |
Mermeriini | Mermiria bivitatta | mb | Arivaca | 9-03‡ | 1 |
Mermiria texana | met | Arivaca | 9-03‡ | 1 | |
no tribe | Acantherus piperatus | ap | Arivaca | 9-03‡ | 4 |
Parapomelini | Parapomala pallida | pp | Prescott Valley | 7-01* | 1 |
Parapomala pallida | pp | Arivaca | 9-03‡ | 3 | |
Oedipodinae | |||||
Hippiscini | Hadrotettix trifasciatus | ht | Prescott Valley | 7-01* | 4 |
Heliastus benjamini | hb | Arivaca | 9-03‡ | 1 | |
Leprus wheeleri | lw | Arivaca | 9-03‡ | 1 | |
Xanthippus corallipes | xc | Prescott Valley | 6-01*,† | 5 | |
Sphingonotini | Conozoa carinata | cc | Arivaca | 9-03‡ | 1 |
Trimerotropis pallidipennis | tp | Prescott Valley | 7-01* | 1 |
Animals used for the scaling study; †animals used for the Pc study; ‡animals used for the ventilation frequency/tidal volume study.
We measured CO2 emission at 25°C as previously described(Greenlee and Harrison,2004a). Briefly, grasshoppers were placed in a respirometry chamber small enough to restrict movement and allowed to acclimate for 20 min before recording began. All animals were measured in normoxia for 3 min to determine normoxic scaling coefficients for CO2 emission. A subset of these species (identified by a dagger in Table 1) was then exposed for 3 min to 10 different levels of PO2 in decreasing order (16,13, 9, 7, 5, 3, 2, 1, 0.5 and 0 kPa O2) to determine the Pc value for each species(Table 1). We identified the Pc for each grasshopper by comparing confidence intervals for CO2 emission at each PO2(Greenlee and Harrison,2004a). A few animals exhibited discontinuous gas exchange in response to hypoxia and were not included in the computation of Pc. To determine whether our short-term exposures produced Pc values representative of steady-state values, we also measured Pc using 1 h exposures to each PO2 for one relatively large (Melanoplus differentialis) and one relatively small (Melanoplus sanguinipes) species.
Body size effects on ventilation frequency and tidal volume index
In a separate study (different individuals and species), we quantified changes in ventilation frequency in response to hypoxia for 15 species of Arizona grasshopper (double dagger in Table 1). Animals were field-collected and maintained as described above. We measured ventilation frequency and tidal volume in 21 and 5 kPa PO2 at 25°C, as we have done previously(Greenlee and Harrison,2004a). Briefly, animals were placed into a respirometry chamber and allowed to acclimate to the chamber for 20 min while the chamber was perfused with air (21% O2, balance N2, flow rate= 400 ml min–1). After the acclimation period, the animal's abdomen was magnified using a dissecting scope and the resulting image videotaped(Panasonic SVHS, Desktop Editor Pro-Line, Secaucus, NJ, USA) for 1–2 min with a Hitachi 3CCD camera (Hitachi, Tokyo, Japan). Magnification was adjusted so that the abdomen nearly filled the monitor, and we recorded a metric ruler for calibration. We then perfused the chamber with 5% O2, 95%N2 for 3 min, after which time we recorded breathing for 1–2 min. Videotapes were played back to a monitor, and we counted ventilation frequency over a 1 min period and measured changes in abdominal height from frame-by-frame analysis of the video.
We calculated tidal volume index as the difference between the inspiratory and expiratory volumes, using an average of three breaths for each individual. For a variety of reasons, this calculated tidal volume should be considered only an estimate for individual species. First, abdominal length measurements were made on pinned specimens and averaged for a species. Second, our prior simultaneous measures of height, width and length changes were made only on Schistocerca americana (Greenlee and Harrison, 1998), and it is possible that different species show different patterns of abdominal compression. Finally, convection in grasshoppers can be enhanced by non-abdominal movements such as neck pumping(Miller, 1960). We calculated our index of ventilation volume (μl min–1) as ventilation frequency×tidal volume.
Phylogenetic analysis and statistics
Typically, scaling relationships are determined by simple regressions, and we used this test here. However, this method assumes that each species mean is an independent point. Because closely related species could be expected to have similar body masses or measured responses to our experimental procedures,we needed to account for phylogenetic effects. The best way to account for ancestry is by using a known phylogenetic tree and calculating branch lengths to weight the relationships between variables(Harvey and Pagel, 1991; Garland, Jr and Adolph, 1994). However, for orthopterans, the phylogeny is largely unknown and untested, and exact branch lengths exist for few species. Therefore, we created a tree(animals identified by an asterisk in Table 1) from previously published works and from taxonomy. For relationships between family, subfamily and tribe, we used Otte and Nasrecki(Otte and Nasrecki, 1997), and for species relationships we used published molecular studies (Chapco et al.,1997; Chapco et al.,1999; Knowles and Otte,2000). Then, we counted the number of branches at the level of family, subfamily, tribe, genus and species between each species pair as a measure of the distance between species(Fagan et al., 2002; Woods et al., 2004). These distance measures were compiled into a matrix, which was held constant, while we compared matrices created for the differences in body mass between each species pair to the differences in respiratory parameters between the same pairs, using partial Mantel tests (PASSAGE software)(Rosenberg, 2001). To test for significance of the correlation, one matrix was held constant while the other was randomized over 999 iterations, and those predicted values were compared to the observed Z statistic. Large values of Z indicate that large differences between species in one matrix were correlated with large differences in the other matrix. For other statistical analyses, we used SYSTAT 10.2.01. For all statistics, our within-experiment type I error was less than 5%. Values are means ± standard errors (s.e.m.)throughout.
Results
Scaling of ṀCO2and Pc
Normoxic CO2 emission rates scaled with body mass to the power 0.92±0.07 (r2=0.90, P<0.0001)(Fig. 1) with masses ranging from 0.61 to 8.34 g. As PO2 decreased, CO2emission rates remained fairly constant down to the Pcvalue (Fig. 2). There was no effect of exposure time on Pc for the smaller species, M. sanguinipes (Table 2) (t=0.7, P=0.5). However, the longer exposures resulted in a slightly higher Pc value for the larger species, M. differentialis (Table 2) (t=–2.3, P=0.049). We found no relationship between the mean Pc and body mass using linear regression (Fig. 3)(F1,11=1.1, P=0.32; average Pc across all species=4.2 kPa). Similarly, when we controlled for phylogeny using the Mantel test, we found no significant relationship between Pc and body mass(Fig. 4; Table 3). There was also no correlation between phylogeny and body mass(Fig. 4) (Mantel test,correlation coefficient=–0.05, P=0.7).
Species . | Exposure time . | Mean Pc . | ṀCO2 (μmol g-1 h-1) at the Pc . |
---|---|---|---|
Melanoplus differentialis | 3 min | 3.1 | 41.0±3.8 |
1 h | 7.2* | 24.0±2.3 | |
Melanoplus sanguinipes | 3 min | 6.1 | 43.2±6.13 |
1 h | 4.2 | 27.6±4.4 |
Species . | Exposure time . | Mean Pc . | ṀCO2 (μmol g-1 h-1) at the Pc . |
---|---|---|---|
Melanoplus differentialis | 3 min | 3.1 | 41.0±3.8 |
1 h | 7.2* | 24.0±2.3 | |
Melanoplus sanguinipes | 3 min | 6.1 | 43.2±6.13 |
1 h | 4.2 | 27.6±4.4 |
Long-term exposure differed significantly from short-term exposure.
. | Mantel test results . | . | Linear regression coefficients . | . | . | . | ||||
---|---|---|---|---|---|---|---|---|---|---|
Respiratory variable (N) . | Correlation . | P . | m . | b . | P . | r2 . | ||||
Pc (13) | n.s. | n.s. | ||||||||
Ventilation frequency | 0.43 | 0.0003 | n.s. | |||||||
21 kPa O2 (15) | ||||||||||
5 kPa O2 (15) | 0.68 | 0.001 | 0.23±0.08 | 1.8±0.03 | 0.02 | 0.34 | ||||
Tidal volume (μl) | n.s. | — | 0.71±0.24 | 1.4±0.09 | 0.01 | 0.44 | ||||
21 kPa O2 (13) | ||||||||||
5 kPa O2 (15) | 0.43 | 0.001 | 0.69±0.28 | 1.5±0.09 | 0.03 | 0.32 | ||||
Ventilation volume (μl min-1) | 0.57 | 0.001 | 1.00±0.20 | 2.93±0.07 | 0.001 | 0.69 | ||||
21 kPa O2 (13) | ||||||||||
5 kPa O2 (15) | 0.59 | 0.001 | 0.93±0.26 | 3.35±0.09 | 0.03 | 0.49 | ||||
Tracheal system conductance (μmol kPa-1 h-1) (13) | 0.81 | 0.001 | 0.73±0.1 | 2.4±0.15 | 0.00 | 0.5 | ||||
Mass-specific conductance (μmol kPa-1 g-1h-1) (13) | -0.56 | 0.001 | -0.28±0.1 | 2.4±0.02 | 0.02 | 0.41 |
. | Mantel test results . | . | Linear regression coefficients . | . | . | . | ||||
---|---|---|---|---|---|---|---|---|---|---|
Respiratory variable (N) . | Correlation . | P . | m . | b . | P . | r2 . | ||||
Pc (13) | n.s. | n.s. | ||||||||
Ventilation frequency | 0.43 | 0.0003 | n.s. | |||||||
21 kPa O2 (15) | ||||||||||
5 kPa O2 (15) | 0.68 | 0.001 | 0.23±0.08 | 1.8±0.03 | 0.02 | 0.34 | ||||
Tidal volume (μl) | n.s. | — | 0.71±0.24 | 1.4±0.09 | 0.01 | 0.44 | ||||
21 kPa O2 (13) | ||||||||||
5 kPa O2 (15) | 0.43 | 0.001 | 0.69±0.28 | 1.5±0.09 | 0.03 | 0.32 | ||||
Ventilation volume (μl min-1) | 0.57 | 0.001 | 1.00±0.20 | 2.93±0.07 | 0.001 | 0.69 | ||||
21 kPa O2 (13) | ||||||||||
5 kPa O2 (15) | 0.59 | 0.001 | 0.93±0.26 | 3.35±0.09 | 0.03 | 0.49 | ||||
Tracheal system conductance (μmol kPa-1 h-1) (13) | 0.81 | 0.001 | 0.73±0.1 | 2.4±0.15 | 0.00 | 0.5 | ||||
Mass-specific conductance (μmol kPa-1 g-1h-1) (13) | -0.56 | 0.001 | -0.28±0.1 | 2.4±0.02 | 0.02 | 0.41 |
Values of m and b are means ± s.e.m.
Correlation coefficients (calculated from partial Mantel tests) between body mass Mb (in g) and respiratory variables when corrected for phylogeny.
Regression equations were calculated as: log(ventilatory parameter)=m(logMb)+b, where m=slope,b=y-intercept. n.s., not significant.
Ventilation frequency, tidal volume index and ventilation volume
Hypoxia response
Three animals had unmeasurable tidal volumes and, therefore, were deleted from this analysis. In general, exposure to hypoxia stimulated ventilatory activity. Ventilatory frequencies (breaths min–1)approximately doubled during hypoxia (repeated-measures ANOVA, F1,12=33.0, P<0.001). Tidal volume (μl breath–1) also increased from normoxia (24.0±4.2) to hypoxia [38.3±9.2; repeated-measures General Linear Model (GLM), F1,11=5.4, P=0.04]. The response of ventilation volume to hypoxia varied for animals with different masses (significant mass×atmosphere interaction, repeated measures GLM, F1,11=5.374, P<0.001).
Scaling of ventilatory parameters
With species means considered to be independent data points, ventilation frequency did not significantly scale with body mass during normoxia, but did increase significantly with mass in 5% O2(Fig. 5; Table 3). However, ventilation frequencies in both 21 and 5 kPa O2 were positively correlated with body mass when phylogeny was held constant(Table 3; Fig. 5). Using linear regressions, both normoxic and hypoxic tidal volumes scaled with mass to the 0.71 and 0.69 power, respectively (Table 3). When phylogeny was taken into account, tidal volume in normoxia was not correlated with body mass. However accounting for phylogenetic relatedness did not change the positive correlation between hypoxic tidal volume and body mass (Table 3). Ventilation volume (μl min–1) increased significantly with mass under both normoxic and hypoxic conditions, with slopes of 1.0 and 0.93, respectively (Fig. 6; Table 3). This pattern was also observed when we corrected for phylogeny.
Maximal tracheal system conductance
Maximal tracheal conductance was calculated from MCO2×P–1c,where MCO2 is the CO2 emission at the Pc (Greenlee and Harrison, 2004a). This calculation assumes that at the Pc, the animal is maximizing gas exchange capacity(spiracles maximally open, tracheal fluid removed, etc.) and that at the Pc, mitochondrial PO2 is indistinguishable from 0 kPa. Maximal tracheal conductance scaled with mass0.73 (Fig. 7; Table 3). Mass-specific conductance decreased with mass, when analyzed with both linear regression and partial Mantel tests (Table 3).
Discussion
Body size effects on Pc
Contrary to a prediction based on the hypothesis that oxygen delivery is more challenging for larger insects, we found that there was no effect of body size on the safety margin for gas exchange in resting grasshoppers (Figs 3, 4). There was considerable variation in Pc among species and within species(O2 range: 2–17 kPa). One possible explanation for the variation is that the age of these field-collected animals was unknown, and previous work has shown that developmental stage can significantly affect Pc (Greenlee and Harrison, 2004b).
Interestingly, longer exposures (1 h vs 3 min) to hypoxia increased the Pc in the larger M. differentialis,from 3.1 to 7.2 kPa (Table 2). Similarly, in a previous study using Schistocerca americana, we found that adults exposed to longer periods of hypoxia had slightly higher Pc values and lower CO2 emission rates(Greenlee and Harrison,2004a). These data suggest that some grasshoppers may have difficulty sustaining metabolism over long hypoxic periods, perhaps because these species rely on anaerobic ATP synthesis or internal oxygen stores to maintain metabolic rates in short term hypoxia. The smaller Melanopline(M. sanguinipes) showed no difference in Pcbetween short or long exposures, but, regardless of duration of exposure, Pc values for the larger species did not differ statistically from those of the smaller species. Therefore, though our data suggest that longer hypoxic exposures increase Pc, there remains no statistical evidence for a reduced safety margin for oxygen delivery in larger resting grasshopper species.
Mechanisms for hypoxia tolerance
How do grasshoppers maintain metabolic rates in hypoxia? Many animals in low oxygen atmospheres increase ventilation frequencies, tidal volumes, or both, resulting in increased ventilation volume(Frappell et al., 1992). Across species, we found evidence for both mechanisms in grasshoppers, with ventilation frequency, tidal volume and ventilation volume all significantly increased by exposure to hypoxia (Figs 5, 6, Table 2). Since ventilation volumes increased threefold as oxygen levels dropped fourfold, other mechanisms are likely to be involved in the preservation of gas exchange. These mechanisms may include decreased tracheolar fluid levels and/or tissue PO2 levels. Drops in tissue PO2 seem most likely to have occurred, since conductance from the tracheae to the tissue does not increase significantly until PO2 values drop below 5 kPa in grasshoppers (Greenlee and Harrison, 1998).
Ventilatory compensation for larger body size in normoxia
Typically, as vertebrates get bigger ventilation frequency decreases, and tidal volume increases isometrically(Peters, 1983). Together the scaling coefficients of these parameters (–0.25 and 1, respectively) sum to the scaling coefficient for absolute metabolic rate (0.75)(Schmidt-Nielsen, 1984). Thus,as vertebrates increase in body mass, mass-specific metabolic needs decrease,and ventilatory frequencies decrease in accordance with those requirements. No prior study has examined such scaling during active ventilation in insects. In contrast to the pattern found in vertebrates, ventilation frequency tended to increase with mass (during hypoxia, and during normoxia when phylogeny was accounted for), and tidal volumes increased, but less than isometrically (not significantly when phylogeny was controlled, scaling with mass0.7). However, as in vertebrates, ventilation volumes and metabolic rates scaled similarly with mass(1 and 0.93). Thus, larger grasshoppers match ventilation to metabolic oxygen need, resulting in similar safety margins for oxygen delivery, at least at rest.
These scaling patterns for abdominal pumping in grasshoppers differed from the scaling of frequencies and volumes of gas emission found for insects exchanging gases discontinuously. During discontinuous gas exchange (DGC),frequencies of spiracular opening did not vary with mass, and the volume of CO2 emitted per burst scaled isometrically with mass in Tenebrionid beetles (Lighton, 1991). In discontinuously ventilating cerambycid beetles, spiracular opening frequency was not correlated with mass and volume of CO2 during the open phase scaled with mass0.37(Chappell and Rogowitz, 2000). In dung beetles, frequency of spiracular bursts increased with mass (scaling exponent=0.56) and the volume of CO2 emitted per burst scaled with mass0.83 (Davis et al.,1999). Finally, across seven weevil species noted to be cyclically, but not discontinuously, ventilating, frequency of CO2bursts did not scale with body mass, although the volume of each burst scaled with mass0.65 (Klok and Chown,2005). Together, these data suggest that patterns of mass-specific scaling of ventilatory parameters are highly diverse in insects and may differ depending on the mode of ventilation.
The effect of body size on ventilatory patterns in this interspecific study also contrasted with our previous work with developing S. americanagrasshoppers. During the ontogenetic study(Greenlee and Harrison,2004a), we found clear evidence for increased tidal volumes and increasing use of convection with age/size. Early instar juvenile grasshoppers have negligible tidal volumes and are likely to be more reliant upon diffusion for gas exchange (Greenlee and Harrison,2004b). In this study, while the increased ventilation frequency with mass suggests increased use of convection in larger species, the lower mass-specific tidal volumes in larger animals, and the observation that ventilation volume scaled similarly with metabolic rates across grasshopper species, suggests that use of convective gas exchange is similar across these species, as found for vertebrate interspecific comparisons(Stahl, 1967; Lasiewski and Calder,1971).
Does atmospheric O2 limit the maximal body size of insects?
At least in these grasshoppers, we found no evidence that larger insects have smaller safety margins for O2 delivery. Perhaps we would see decreased safety margins if we looked at the largest extant insects; the largest grasshopper species now alive exceed 10 g(Carbonell, 1984) and the largest beetles approach 100 g (Williams,2001). There is evidence that larger insects have decreased safety margins during times of high energy use, such as during flight or terrestrial locomotion (Rascón and Harrison,2005; Harrison et al.,2006), so perhaps examination might find a positive body size effect on Pc during flight. However, the only study to examine Pc during locomotion in insects found that oxygen delivery capacities increase strongly with age/size during jumping of grasshoppers (Kirkton et al.,2005). Thus the evidence to date suggests that larger insects overcome potential diffusion limitations by matching tracheal system conductance to tissue needs, thus maintaining constant safety margins for O2 delivery across size.
Even though we found no evidence for decreasing safety margins for oxygen delivery in larger insects, maximal insect body size could still be affected by atmospheric oxygen levels. For example, increased O2availability could increase growth rates and body size, as in the mealworm, Tenebrio molitor, (Loudon,1988; Greenberg and Ar,1996) and fruitflies (Frazier et al., 2001). Additionally, it is conceivable that even if natural selection operates to maintain constant safety margins for gas exchange across insect sizes, that the ability of convection to compensate for large size might reach some limit. For example, if convective gas exchange is increased by increasing the volume of tracheal air sacs across species, as may occur in developing grasshoppers (Greenlee and Harrison, 2004a; Lease et al., 2006), it is conceivable that at some large size the volume of air sacs required might exceed available internal space. In support of this argument, the largest living beetles have been reported to have a huge fraction of their body filled with tracheae and air sacs(Miller, 1966). Higher atmospheric oxygen levels might then facilitate gigantic insects by allowing similarly sized tracheae and air sacs to deliver more oxygen, since tracheal proliferation and dimensions are decreased by hyperoxic rearing(Jarecki et al., 1999; Henry and Harrison, 2004).
Acknowledgements
This work was supported by grants NSF IBN-9985857 and IOB 0419704 to J.F.H., EPA U91616501 to K.J.G., NSF IBN-0206678 to K.J.G. and J.F.H., and a Sigma Xi Grant In Aid of Research to K.J.G. We would like to thank Jeffrey R. Hazel, Michael C. Quinlan, Ronald L. Rutowski and Glenn E. Walsberg for their comments on this manuscript. In addition, we would like to thank Brenda Rascón and Dave Brown for help with grasshopper collection, and Patricia Coulter for some of the Pc data collection.