Climatic changes can induce geographic expansion and altitudinal shifts in the distribution of invasive species by offering more thermally suitable habitats. At the remote sub-Antarctic Kerguelen Islands, the predatory insect Merizodus soledadinus (Coleoptera: Carabidae), introduced in 1913, rapidly invaded coastal habitats. More recent colonisation of higher elevation habitats by this species could be underlain by their increased thermal suitability as the area has warmed. This study compared the effect of elevational range shift on the morphology and physiology of adult M. soledadinus sampled along two altitudinal transects (from the foreshore to 250 m a.s.l.) and a horizontal lowland transect orthogonal to the seashore (400 m length). Although high inter-individual and inter-transect variations in the traits examined were present, we observed that body mass of males and females tended to decrease with elevation, and that triglyceride contents decreased with distance from the shore. Moreover, protein contents of females as well as those of 26 metabolites were influenced significantly by distance to the foreshore. These results suggest that future climate change at the Kerguelen Islands will further assist the colonisation of lowland inland and higher altitude habitats by this aggressively invasive predator, by making previously sub-optimal habitats progressively more suitable.
The geographic distributions and abundances of ectothermic groups such as insects are shaped in part by climatic conditions. In the current context of rapid global and regional climatic changes, altitudinal and latitudinal range shifts have been documented for various ectothermic taxa1,2,3. Moreover, increasing air temperature may favour human-assisted translocation and establishment of alien insects into new geographic areas4,5. Climate change can increase both survival and functional capabilities of introduced insects6, and may lower or remove barriers to invasion1,4,7,8,9. Changing climatic conditions can also facilitate the establishment of alien insects indirectly by altering community assemblages10,11,12,13 and increasing niche availability14.
In parts of the polar regions, contemporary climatic changes are occurring more rapidly than elsewhere, and greatly modify climate envelopes from micro- to macro-geographical scales15,16,17. These changes are opening opportunities for newly arrived species to successfully establish10, and in some cases become invasive10,18,19,20. The sub-Antarctic Kerguelen archipelago is no exception, with mean air temperatures that have increased by 1.7 °C over the period 1951–2010, while precipitation has decreased drastically since the 1990s20. The establishment and geographic spread of aphids, the blowfly Calliphora vicina and the carabid beetle Merizodus soledadinus on the archipelago have likely been assisted by these changing conditions20,21.
The predaceous M. soledadinus was introduced from the Falkland Islands to the Kerguelen archipelago in 191322,23. In the archipelago, this insect preferentially feeds on fly larvae24, and has year-round activity25. The main habitat conditions within the natural distribution of M. soledadinus (Falkland Islands, Patagonia) overlap at least partly with the climatic conditions at the Kerguelen Islands18,26, which suggests that this wingless beetle was likely physiologically pre-adapted to the chronically cool oceanic climate of the archipelago. Adult beetles perform well at cool temperatures, although the studies of Lalouette et al.27 and Laparie and Renault21 both suggest that the insects are currently in the lower part of their thermal comfort zone at the Kerguelen Islands.
Long-term monitoring of the distribution of M. soledadinus in the Kerguelen archipelago revealed that its geographic distribution and population expanded rapidly in the early 1990s20,24. The beetle now has a large range, occupying many coastal areas and expanding along hydrographic networks28, where trophic resources and water are available. Recently, populations of M. soledadinus have colonised habitats at higher altitude29, with individuals now being found up to 400 m above sea level (a.s.l.), where environmental conditions were previously assumed to be unfavourable. Nowadays, mean annual temperature at 400 m a.s.l. ranges between 3 °C and 4 °C30, with a temperature lapse rate of 0.6–0.7 °C per 100 m increase in altitude typical in alpine regions and at the sub-Antarctic islands30,31,32. Thus, the mean annual temperature at 400 m a.s.l. is likely to have ranged between 0.3 °C and 2.3 °C in the 1950s at the Kerguelen Islands. Even though arthropod diversity generally progressively declines with increasing altitude, as reported for mites and springtails on Marion Island33 and for aphids at the Kerguelen Islands34, the distribution of the potential arthropod prey of M. soledadinus should also be altered with climate warming along altitudinal gradients35.
The recent altitudinal expansion of M. soledadinus in the archipelago may be the result of progressively more suitable thermal conditions being experienced at higher altitudes, which may in addition be associated with potential prey (introduced and native Diptera larvae, annelids, micro-arthropods) expanding their ranges toward higher altitudes. If the geographic expansion of M. soledadinus towards higher altitude habitats is primarily driven by the movement of a suitable climatic envelope, i.e. the progressive colonisation of suboptimal altitudinal habitats, we would expect to observe the accumulation of cold-stress molecular markers in this insect. In this work, we thus compared the physiological characteristics of adult M. soledadinus along altitudinal invasion gradients, by sampling beetles along two replicated transects from the foreshore (0 m a.s.l.) to 250 m a.s.l. An additional horizontal transect (400 m horizontal transect orthogonal to the seashore) was completed to take into account the general reduction in the abundance and diversity of trophic resources with increasing distance from the seashore, and possible impacts on the morphology and physiology (body size, body composition, metabolic phenotypes) of the adult beetles. For all sampled insects, morphological traits and total concentrations of three general reserve compounds in insects (proteins, triglycerides and glycogen) were measured. Metabolic phenotypes of M. soledadinus adults were compared among insects sampled at known altitude and/or proximity to the coast via Gas Chromatography – Mass Spectrometry analyses (GC-MS). As we hypothesised that range expansion reflects recent climate change, we predicted that higher altitudes should be associated with an increase of adult body size (temperature-size rule). In parallel, we also predicted differentiation of metabolic phenotypes between lowland and highland beetles, in particular for compounds involved in glycolysis and the tricarboxylic acid cycle that are likely to be affected by habitat temperature, and the accumulation of cold stress markers in the form of polyols or free amino acids.
Morphological changes along the transects
Males of M. soledadinus were characterised by smaller body size than females (F = 109.77, df = 1, P < 0.001, NMales = 287, NFemales = 196, see Fig. 1 and Supplementary Table S1 and S2), exemplified by the elytra length of females measuring 3.44 ± 0.17 mm (mean ± SD), while those of males were 3.29 ± 0.16 mm. Body size was not significantly influenced by altitude (F = 0.019, df = 1, P = 0.89, NMales = 149, NFemales = 117), despite body mass of both males and females decreasing with altitude (Supplementary Table S1 and S2). Individuals sampled closer to the shore had larger body sizes than those sampled further inland (F = 8.34, df = 1, P = 0.004, N = 485). A positive but marginally non-significant effect of longitude (F = 7.14, df = 1, P = 0.07, NStMalo = 114, NMolloy = 152, NAnsePapous = 219) highlighted possible inter-site differences, with an eastward increase in body sizes of individuals (St. Malo < Molloy < Anse des Papous).
Variations in glycogen, protein and triglyceride contents
The glycogen contents of the samples were not affected by any of our explanatory variables (Altitude: F = 0.59, df = 1, P = 0.44, N = 158; Coast proximity: F = 2.01, df = 1, P = 0.16, N = 238; Sex: F = 2.78, P = 0.097, NMales = 130, NFemales = 108).
Females had significantly higher amounts of proteins than males (F =205.19, df = 1, P < 0.001, NMales = 130, NFemales = 108, see Fig. 2). Individuals of both sexes sampled in proximity to the shore had higher amounts of proteins (F = 4.14; df = 1, P = 0.04, N = 238). The significant interaction between altitude and sex (F = 4.33, df = 1, P = 0.04, N = 238) highlighted distinct responses depending on the sex, as female protein content decreased with increasing altitude, while protein content remained stable in males. A significant interaction between sex and longitude (F = 12.78, df = 1, P < 0.001, N = 238) again highlighted possible site-specific differences between the two sexes: at the transects completed at Anse des Papous and Molloy, protein amounts were very distinct between males and females, while at St. Malo the values were more similar. However, this difference might also be an artefact of the reduced number of sampling sites from which females were obtained in the St. Malo transect.
Finally, proximity to the coast had no effect on triglyceride content (F = 2.35, df = 1, P = 0.13, N = 100), while triglyceride content co-varied negatively with altitude (F = 19.74, df = 1, P < 0.001, N = 70, see Fig. 3). The significant effect of longitude (F = 19.26, df = 1, P < 0.001, N = 100) again highlighted site-specific responses, as individuals collected from the two altitudinal transects had higher amounts of triglycerides than those from the horizontal transect.
The total amounts of metabolites of three metabolic families (free amino acids, organic acids and polyols) were significantly influenced by altitude. Beetles sampled at 0, 200 and 250 m a.s.l. had higher amounts of free amino acids (F = 4.04, df = 1, P = 0.048, N = 59) and polyols (F = 6.64, df = 1, P = 0.012, N = 59) than found in beetles sampled at the intermediate points at 50, 100 and 150 m a.s.l. (Fig. 4). The amounts of organic acids were positively correlated with altitude (F = 12.49, df = 1, P < 0.001, N = 59), with a regular increase from 150 m upwards in the beetles sampled along the St. Malo transect, and concentration peaking in beetles from the Molloy transect sampled at 200 m a.s.l.
Samples collected near the coast had increased amounts of total free amino acids relative to those collected further inland (F = 5.89, df = 1, P = 0.017, N = 91); this difference was strongly influenced by the lower amounts measured in the beetles sampled at 400 m inland along the horizontal Papous transect. Longitude effects on metabolic family contents were also found, as beetles sampled along the horizontal transect had higher amounts of free amino acids (F = 6.29, df = 1, P = 0.014, N = 91) compared with the altitudinal transects, and beetles from the St. Malo transect had lower amounts of polyols (F = 11.21, df = 1, P = 0.0012, N = 91) compared to the other transects. None of our explanatory variables had significant effects on the amount of sugars (coast proximity: F = 1.81, df = 1, P = 0.18, N = 91; altitude: F = 0.03, df = 1, P = 0.86, N = 91; longitude: F = 0.23, df = 1, P = 0.63, N = 91).
The MANOVA performed on the matrix of 42 compounds revealed significant effects of altitude (approx. F42,45 = 2.87, P < 0.001, N = 91), coast proximity (approx. F42,45 = 2.61, P < 0.001, N = 91) and the interactions between coast proximity and longitude (F42,45 = 2.6, P < 0.001, N = 91) on individual metabolite concentrations. Changes in the concentrations of the 42 detected and quantified metabolites along each transect are presented in Fig. 5. The amounts of 26 metabolites were influenced by the sampling distance to the foreshore (Supplementary Table S3). Fourteen metabolites, including 10 free amino acids (Supplementary Table S3), were significantly influenced by both coast proximity and longitude. This result was mainly due to low levels of GABA, glutamate, lysine and threonine quantified from the beetles from the Anse des Papous transect sampled at 400 m inland (Fig. 5, Supplementary Table S3). Conversely, beetles sampled at 200 and 250 m a.s.l. along the altitudinal transects displayed high levels of several metabolites (Supplementary Table S3). Three metabolites (citrate, lactate and galacturonate) co-varied positively with altitude. Inter-site variations were found, with decreased levels of arabinose, galactitol and gluconolactone in samples from the St. Malo transect, while beetles sampled along the Anse des Papous transect had increased levels of fructose, glycerol-3-phosphate (glycerol3P), pipecolate, putrescine and serine compared to the altitudinal transects (Supplementary Table S3).
Metabolic variations were further examined for each transect separately in order to assess if similar patterns could be observed among transects when the sampling groups were discriminated with LDA. For Anse des Papous, the first axis of the LDA (37.2% of the total variance) separated the samples collected at 0 and 400 m inland from those collected at 100 and 200 m inland (Fig. 6a). This discrimination was partly explained by higher amounts of galactose and glycerol-3-phosphate in the two latter insect groups. The second axis (34.7% of the total variance) sorted the groups according to the distance from the initial sampling point. This axis was mainly supported by the co-varying metabolites pipecolate and succinate (only pipecolate is represented on the LDA, as these two compounds have >80% correlation), whose concentrations were increased in groups closest to the coast. Conversely, higher mannitol concentrations were measured in groups sampled furthest from the coast.
For the altitudinal transect conducted at Molloy, the first axis of the LDA accounted for 27% of the total variance and separated the 150 and 250 m a.s.l. sampling points (Fig. 6b). Insects sampled at 150 m a.s.l. had higher amounts of galactose, fructose, glycine and malate. On the second axis (24.5% of the total variance), beetles from groups sampled at 0 and 100 m a.s.l. were separated from those sampled at 150 and 250 m a.s.l., the latter being characterized by increasing concentrations of galacturonate and pipecolate. On both axes, the groups sampled at 50 m and 200 m a.s.l. overlapped.
In the second altitudinal transect (St. Malo, Fig. 6c), the first axis of the LDA (26.2% of the total variance) generally separated the sampling groups along the altitudinal gradient. The second axis (22.6% of the total variance) discriminated the insects sampled at 200 m a.s.l. from the other sampling points, due to increased amounts of arabinose, galactose, mannitol and sorbitol in the former group.
The carabid beetle M. soledadinus is a successful invasive species at the Kerguelen Islands20,28. Its geographic distribution was restricted to coastal areas for many decades after its introduction29 but, since the early 2000s, it has been recorded increasingly frequently at higher altitudes. In the present study, we hypothesised that the ongoing colonisation of altitudinal habitats over the past decade results from increased habitat suitability due to altered thermal conditions through the climatic changes occurring in the archipelago20.
Both coast proximity (used to differentiate the higher amount of trophic resources available in the first 200 m away from the seashore, compared to further inland) and altitude had effects on the morphology and physiology of adult M. soledadinus, revealing an overall lower quality of individuals sampled further from the coast and at altitude. Even though significant climate warming has occurred since the 1950s at the Kerguelen Islands, this does not alter the altitudinal temperature decrease of 0.6–0.7 °C for each increase of 100 m in elevation in the sub-Antarctic islands30,32, with the rate of thermal decrease being the greatest from 0 to 150 m a.s.l.36. Temperature is therefore expected to decrease by 2.4 to 2.8 °C between sea level and the highest sampling point in our experimental design. As mean monthly soil temperatures are less than 3.8 °C for 6 months of the year, and less than 2.4 °C for 4 months in lowland habitats27, specimens of M. soledadinus sampled above 150 m a.s.l. must spend a significant part of the year at temperatures around 0–1 °C. These thermal conditions are restricting for an insect whose acute thermal sensitivity in this thermal range has been reported previously: metabolic activity and efficiency of adult M. soledadinus are considerably reduced when temperature falls to around 4 °C27, and thermal conditions become increasingly suboptimal for adult M. soledadinus as temperatures approach 0 °C21,27. Despite ongoing climatic changes, and as expected, it is therefore very likely that adult M. soledadinus at higher levels in the two altitudinal gradients still experience significant temperature-imposed resource and physiological limitations.
Triglyceride contents were overall higher in the two altitudinal transects compared to the horizontal one. This finding could indicate energetic adjustments according to the nature of prey available in horizontal versus altitudinal transects. Consistent with this surmise, diet-related differences have previously been measured in the body composition of adult M. soledadinus21.
Triglyceride amounts of both sexes, and protein amounts of females, decreased with altitude. In a previous study, we did not observe variations in the total number of eggs carried by female M. soledadinus over the year25, and they may be capable of multiple egg maturation cycles. At the Kerguelen Islands, trophic resources become more patchy and sporadic at higher altitudes, limiting nutrient availability for the voracious adults of M. soledadinus. In females, the reduction of available resources may explain the lower amounts of triglycerides and proteins, as the production of vitellogenin and other yolk- and egg-related compounds are energy-demanding. In parallel, the structure and abundance of vegetation changed along the two altitudinal transects: from grassland dominated by Poa annua (itself a non-native species) at sea level, through continuous cover of Acaena magellanica at mid-levels, and progressively becoming scarcer and patchy in rocky fellfields at 250 m a.s.l. (Day E., Laville L., pers. obs). Changes in vegetation cover are known to impact the structure and diversity of invertebrate communities37, in turn potentially affecting trophic resources qualitatively and quantitatively for both larvae and adults of M. soledadinus. As thermal and trophic resources are more restricting with increasing altitude, resource limitation may have progressively reduced the capacity for energy storage, a finding that is also consistent with the reduction of body mass of the insect along the elevation gradient.
A range of studies have reported decreases in development rates in insects of similar size when energy assimilation is restricted (e.g.38,39,40, and this may result in a progressive reduction in body size along altitudinal gradients41,42. Larger insects may require a prolonged developmental time, which may be disadvantageous for insects thriving at higher elevations who experience shorter active seasons, and more particularly for the non-diapausing species that cannot develop over multiple years43. At the sub-Antarctic Heard Island, Chown and Klok2 observed that body size of weevils decreased with altitude, but this finding contrasted with the pattern reported for these insects from Marion Island. In our study, we did not observe changes in the body size of adult M. soledadinus sampled along the altitudinal gradients, while body mass progressively reduced. Where resource limitation occurs, either resulting from thermally-induced constraints or lower availability of trophic resources, the rate of growth of juvenile insects, which is partly driven by protein synthesis44, should proceed more slowly. As the body size of M. soledadinus from the altitudinal gradients was similar to those from the lowland transect, this suggests that the duration of development may be extended in altitudinal habitats.
Several essential amino acids, including isoleucine, leucine, methionine, phenylalanine, tryptophan, threonine and valine, were present in lower amounts in the beetles as distance to the coast increased (>400 m for the horizontal transect, most often from >50 m for the altitudinal transects). Nutrient limitation in essential amino acids can greatly constrain fecundity45, as these metabolites contribute a significant proportion of egg carbon content. Our data may suggest a higher food intake by adult M. soledadinus from habitats near the coast, an assumption which is consistent with the variation in protein concentration which reduced as the distance to the coast increased. Furthermore, amino acids represent a key source of nitrogen for insects, and nutrient limitation during the larval stage can have significant consequences on the phenotypic traits of the adult, by modifying developmental rates, which in turn affects fitness46. Indeed, several proteins of larval origin are further catabolised by female insects during egg production45,47, while additional latent effects of nutrient limitation during larval stages can also be expected, affecting adult immune function, reserve compound storage, or increasing oxidative stress46.
The overall inter-site metabolomic comparison revealed that insects from the three transects were characterised by distinct metabolic phenotypes, despite the relatively small geographic distances separating them. Metabolic phenotypes of the specimens from the two altitudinal transects (Molloy and St. Malo) did not overlap, further suggesting that insects experienced distinct ecological conditions along these two transects. Beetles sampled from the St. Malo transect were characterised by higher amounts of polyols and of four metabolites including two amino acids (GABA and glycine) compared to the two other transects. Thermal conditions may be more limiting in this site, St. Malo being closer to the western part of the archipelago, where the climate is colder and wetter. The progressive increase in amounts of polyols is consistent with this hypothesis, as these compounds are typically involved in the physiology of cold tolerance in insects48. St. Malo is also the site M. soledadinus colonised earliest of those examined in this study (known to have been present since 199624). This longer period of local presence may have had a greater impact on the prey community, by altering qualitatively and quantitatively the available trophic resources.
Metabolic phenotypes of adult M. soledadinus from the horizontal transect (Anse des Papous) strongly differed between the insects collected at 0 and 100 m (the latter grouped with the metabolic phenotypes of adult M. soledadinus sampled at 200 m), and from those sampled 400 m from the coast. The insects obtained close to the coast (0 m) were characterised by high amounts of the metabolites inositol and pipecolate. At this sampling site, carabid beetles can thrive in concentrations of marine debris where salinity ranges from 35 to 70 parts per thousand, thus imposing osmoregulatory constraints to individuals. Insects exposed to saline conditions often accumulate specific osmolytes49, including inositol or pipecolate, as previously reported by Hidalgo et al.50 in adult M. soledadinus experimentally subjected to increasingly saline conditions. When sampled 400 m from the seashore, beetles exhibited lower concentrations of amino acids, tricarboxylic cycle intermediates and sugars as compared with those from the three other groups. Even in the absence of data on the metabolic rates of these specimens, this result may be explained by a reduced activity of energetic metabolism resulting from the lower availability of trophic resources. Consistently, the concentrations of three (free amino acids, intermediate acidic metabolites and amines) out of the four defined metabolic families in insects from the 400 m sample from the horizontal transect were similar to the pattern that has been observed for adult M. soledadinus sampled along the altitudinal transects.
The separation of the M. soledadinus’ groups sampled along the two altitudinal transects was generally similar. First, carabid beetles sampled at the coast differed from the other sampled insects. Second, beetles sampled at higher elevation (200 m a.s.l. – St. Malo only - and 250 m a.s.l.) were distinct. In adult M. soledadinus sampled at 200 and 250 m a.s.l., the concentrations of free amino acids, and also intermediate acidic metabolites and polyols were increased as compared with carabid beetles from lowland habitats (50 m a.s.l.). These physiological responses have been reported previously in a large range of insect species subjected to cold temperatures51,52, including adults of M. soledadinus21. Higher levels of free amino acids are often considered as a reliable marker of thermal stress in insects, thus supporting the hypothesis of less favourable thermal conditions for adult M. soledadinus thriving at 200–250 m a.s.l at the Kerguelen Islands. Interestingly, we also found that the ranking of the insects from the two sampling sites, St. Malo and Molloy, was similar in the two altitudinal gradients, with a gradient of lower to higher altitudinal sampling sites along the first axis. It is very likely that decreasing temperatures along the two altitudinal transects represent a significant force shaping in a similar manner the physiology of adult M. soledadinus. At intermediate elevations, metabolic responses of the insects exhibited important inter-site variations, most probably resulting from the specific micro-environmental characteristics of the habitats and from inter-individual variation (age, sex, reproductive status, nutritional status at the time of collection). Of note, an individual collected at a given sampling point may have not spent its entire life at this point and may have moved to lower or higher elevation after its emergence (although larvae are likely to have much lower dispersal abilities compared with adults). Although this phenomenon would act to blur some of the interpretations made, our data suggest that its occurrence is not sufficiently frequent to override all patterns along transects.
Recent climatic changes in the Kerguelen archipelago have positively influenced the invasion process of M. soledadinus both at lower altitude locations where populations of this species were largely absent before 2003, and at higher altitudes. Taken together, our data suggest that specimens collected along altitudinal transects are characterized by distinct physiological condition as compared with their lowland counterparts, supporting the idea of the colonisation of suboptimal highland habitats becoming gradually more suitable. Yet, thermal conditions remain suboptimal, and M. soledadinus sampled at higher altitudes most probably continue to experience significant temperature-imposed resource and physiological limitations, as revealed for instance by the accumulation of cold-stress molecular markers. Our data thus suggest that, if current temperature increase trends continue, this insect will likely flourish at its currently colonised altitudinal limits, and could even progress and colonise higher altitudes (given the availability of suitable habitat and trophic resources), while also extending its geographical distribution westwards, towards the currently colder, wetter and ice-capped part of the archipelago.
Materials and Methods
Insect sampling along environmental gradients
Adult M. soledadinus were hand-collected under stones in March 2013 at the Kerguelen Islands at three distinct localities: Molloy, St. Malo and Anse des Papous (Supplementary Fig. S1 and Table S4). At Molloy and St. Malo, two altitudinal transects were sampled, starting from the foreshore (0 m a.s.l.) and continuing up to 250 m a.s.l.; in both locations, beetles were sampled at 50 m elevational intervals along the transect (N = 6 sampling sites for each transect). At Anse des Papous, a horizontal low altitude transect was completed away from the seashore. This transect included eight sampling sites (0, 50, 100, 150, 200, 250, 300 and 400 m inland). At each sampling site, GPS coordinates were recorded, and a total of 86 adult M. soledadinus were collected: 50 individuals were sampled for morphometric and colorimetric assays (total protein and glycogen), 18 individuals (six replicates of three beetles) were collected for triglyceride assays, and 18 individuals (six replicates of three beetles) for GC-MS analyses. Upon collection, insects were directly plunged into microtubes containing 1 mL of 96% ethanol, and stored at −20 °C before further analyses. The physiology of insects may vary on a daily basis, depending on field conditions (e.g. temperature, relative humidity) or trophic status. As a result, particular attention was given to the meteorological conditions, and insect sampling was only carried out on days with similar weather (no rain, wind below 25 km/h, air temperature at the research station between 9 and 12 °C). Finally, insects were collected in the morning of three consecutive days to average environmentally-induced noise and limit possible effects of any circadian rhythm on the physiology of the insects.
At each sampling site, 25 individuals (from the 50 sampled beetles) were randomly selected, except for specimens sampled at St. Malo at 0, 50 and 250 m a.s.l. for which only 12, 21 and 6 beetles were available, respectively. Sex of each beetle was determined under a stereo microscope. As often observed for the species at the Kerguelen Islands, sex ratio was biased toward males in 75% of the samples, and it was necessary to include additional females for the Anse des Papous transect (0, 100, 150, 250 and 300 m sampling sites). Pictures of each beetle were taken with a video camera (AxioCam ERc 5 s, ZEISS, Germany) connected to a stereo microscope. Inter-ocular distance, width and length of the thorax, length of the right elytra (Fig. 7) were measured by vectorial layouts with AxioVison software (repeatability was verified using a set of 20 individuals measured twice for each morphological trait: the mean proportion difference was 0.9, 2.6, 2.4 and 2.9 for inter-ocular distance, width and length of the thorax and right elytra length, respectively. Beetles were subsequently vacuum-dried for 15 h (Speed Vac Concentrator, MiVac, GENEVAC LTD, Ipswich, United Kingdom), before being individually weighed (Balance XP2U METTLER TOLEDO, Columbus, OH, d = 0.1 µg).
Protein, glycogen and triglyceride contents
Body composition was determined from insects from the six sampling sites (0, 50, 100, 150, 200 and 250 m a.s.l.) from Molloy and St. Malo (altitudinal transects). For Anse des Papous (horizontal transect), body composition was determined from insects from five sampling sites (0, 100, 200, 300, and 400 m).
Protein and glycogen assays were performed following the protocol developed by Foray et al.53, which allows measurements of total protein and glycogen contents from the same sample. These analyses were conducted on the individuals that were used for morphometric assays. To have comparable sample numbers, six males and six females whose dry mass was distributed between the first and the third quartiles of the sample dry mass distribution were processed for each sampling site. Because of the biased sex ratio toward males in the samples, only three sampling sites of the St. Malo transect contained enough females to perform the assays (100, 150 and 200 m). Samples were homogenised in 180 µL of phosphate buffer for 90 s at 25 Hz using a bead-beating device (RETSCH MM301, RETSCH GBMH, Haan, Germany). Following low-spin centrifugation (180 g, 4 °C), 10 µL of the supernatant was used to measure body protein content using Bradford's technique, as described in Foray et al.53. Absorbance of the samples was read at 595 nm. The quantity of protein was calculated from a bovine serum albumin (CAS number: 9048–46–8) calibration curve. The remaining 170 µL of each sample was mixed with 20 µL of a solution of 20% Na2SO4 and 1200 µL of methanol-chloroform [ratio 2:1, volume:volume]. Samples were centrifuged (180 g, 4 °C) to precipitate glycogen into the pellet. Glycogen concentration was measured through a reaction with 70% anthrone (CAS number: 90-44-8), and the absorbance was read at 625 nm. Glycogen concentration in the samples was calculated based on a glucose standard calibration curve.
For the triglyceride assays, samples consisted of three hand-collected individuals. Six replicates were processed for the six sampling sites of Molloy and St. Malo (except for altitudes 0 and 150 m a.s.l. at St. Malo, for which only five replicates were available), and for five sampling sites of Anse des Papous (0, 100, 200, 300 and 400 m). We used the analytical procedure described in Laparie et al.54. Briefly, samples were vacuum-dried and weighed before being homogenised in 1050 µL of methanol-chloroform [ratio 1:2, volume:volume] for 90 s and 25 Hz using a bead-beating device. After centrifuging, a volume of 600 µL of the lower phase (chloroform + lipids) was transferred to clean microtubes and dried overnight in a fume cupboard. The lipid droplet was re-dissolved into 200 µL of Triton-BSA buffer and incubated for 10 min at 60 °C immediately before the assays. The manufacturer's instructions were followed for the triglyceride colorimetric assays (Triglycerides, kit reference CC02200, LTA SRL, Italy).
GC-MS analyses: sample preparation and derivatisation
Environmental metabolomics has proven a powerful tool in the determination of insect-environment interactions (see reviews by55,56). Field-sampled organisms are expected to show high inter-individual variability, which we attempted to reduce by working on pools of three insects. Concentrations of non-structural carbohydrates, polyols, amino and organic acids were measured using a GC-MS platform as described in Khodayari et al.57. Analyses were carried out on pools of three hand-collected carabid beetles (N = 6 replicates for Molloy and St. Malo, and N = 5 replicates for Anse des Papous) to describe the metabolic phenotypes of adults from 17 sampling sites. Dried insect samples were re-dissolved in 600 µL of methanol-chloroform (ratio 2:1, volume:volume) and homogenised using a bead-beating device (RETSCH MM301, RETSCH GBMH, Haan, Germany) at 25 Hz for 90 s. A volume of 400 µL of ultrapure water was added to the samples that were then further centrifuged for 10 min at 4000 g and 4 °C. Then 90 µL of the supernatant, which contained polar metabolites, was transferred to new microtubes, and these aliquots were vacuum-dried (Speed Vac Concentrator, MiVac, GENEVAC LTD, Ipswich, United Kingdom). Dried samples were re-suspended in 30 µL of 20 mg mL−1 methoxyamine-hydrochloride (CAS Number: 593-56-6, SIGMA-ALDRICH, St Louis, MO, USA) in pyridine prior to incubation under orbital shaking at 40 °C for 60 min. Following incubation, 30 µL of N-methyl-bis(trifluoroacetamine) (BSTFA, CAS Number: 685-27-8) was added, and derivatisation was conducted at 40 °C for 60 min under agitation. Then, 1 µL of each sample was injected using the split mode (25:1). Calibration curves were run for 62 pure reference compounds at concentrations of 1, 2, 5, 10, 20, 50, 100, 200, 500, 750, 1000 and 1500 µM.
For the three transects, samples collected from the foreshore are referred to henceforth as the ‘initial sampling point’. For each transect, the Euclidian distances between the initial sampling point and all other sampling points were calculated from the georeferenced coordinates. In order to investigate the effect of resource rarefaction with progression inland from the seashore, variables measured in individuals sampled from 0 to 200 m (coast proximity) were compared with measurements in individuals sampled beyond 200 m inland. This threshold was selected because it corresponds to the limit of seashore influence in similar environments58, which was corroborated by NDVI (Normalised Difference Vegetation Index) data from the Kerguelen archipelago, that decrease from the shore to 200 m inland, and stabilise further inland59. Site effect was not directly included as an explanatory variable because of its correlation with altitudinal variations; given the clustered coordinates along the coast, longitudinal effect was used as a proxy for inter-site differences.
Linear models were used to assess the effect of altitude, coast proximity, sex (if available) and z-scaled spatial coordinates on each of our measured variables (body size, protein, glycogen and triglyceride amounts), including the interactions between sex and the other variables, as well as between coast proximity and longitude (inter-site variations of coast proximity effect were considered). Interpretations of interactions were carried out using the visreg package60 and non-significant interactions were dropped. All morphological measurements were computed so that we obtained a general measure of body size. This computed body size value corresponds to the coordinates of the projection of the morphological measurements of each individual on the first axis of a Principal Component Analysis (FactoMineR package61), which accounted for 67.4% of the total variance.
Forty-six metabolic compounds were identified via the GC-MS procedure. Concentrations were homogenised (nmol.mg−1 of individual dry mass) and four molecules (cadaverine, ornithine, quinate, and ribose) showing extreme variations of concentrations in various samples were removed from subsequent analyses. First, we tested the effect of altitude, coast proximity and z-scaled spatial coordinates on individual metabolite concentrations. MANOVAs were performed to test for potential differences among experimental groups. Second, total metabolite amounts were summed for four chemical families (free amino acids, N = 16; organic acids, N = 8; polyols, N = 8; and sugars + phosphorylated sugars, N = 5; Supplementary Table S3) for each sampling site. Linear models were then used to compare the amounts of each metabolite family according to altitude, coast proximity and z-scaled spatial coordinates. Third, the concentration of each metabolite was log-transformed to normalise the distribution of model residuals. Linear discriminant analyses (LDA, MASS package62) were then run on individual metabolites sharing less than 80% correlation (N = 27 metabolites). Statistical significance of discrimination was confirmed using the Monte-Carlo permutation test (P < 0.001; 10,000 permutations). In a first LDA, we plotted the metabolic phenotypes of adult M. soledadinus from the three transects. This LDA revealed that our dataset of 27 metabolic compounds was better discriminated transect by transect, with 52.1% of the total variance being explained by the first axis (the between-group inertia being 10.7 times higher than the within-group inertia), and 47.8% by the second axis (Supplementary Fig. S2). LDA analyses were then performed for each transect. The distribution of model residuals was checked using QQ plots and Shapiro-Wilk tests for multivariate normality.
All analyses were carried out with R 3.3.0 statistical software63.
The datasets generated during and/or analysed during the current study are available from the corresponding author on reasonable request.
Walther, G.-R. et al. Ecological responses to recent climate change. Nature 416, 389–395, https://doi.org/10.1038/416389a (2002).
Chown, S. L. & Klok, C. J. Altitudinal body size clines: latitudinal effects associated with changing seasonality. Ecography 26, 445–455 (2003).
Hickling, R. et al. The distributions of a wide range of taxonomic groups are expanding polewards. Glob Change Biol 12, 450–455, https://doi.org/10.1111/j.1365-2486.2006.01116.x (2006).
Renault, D., Laparie, M., McCauley, S. J. & Bonte, D. Environmental adaptations, ecological filtering and dispersal, central to insect invasions. Annu Rev Entomol 63, 345–368 (2018).
Robinet, C. & Roques, A. Direct impacts of recent climate warming on insect populations. Integr Zool 5, 132–142, https://doi.org/10.1111/j.1749-4877.2010.00196.x (2010).
Hellmann, J. J., Byers, J. E., Bierwagen, B. G. & Dukes, J. S. Five potential consequences of climate change for invasive species. Conserv Biol 22, 534–543, https://doi.org/10.1111/j.1523-1739.2008.00951.x (2008).
Charnov, E. L. & Gillooly, J. F. Thermal time: body size, food quality and the 10 degrees C rule. Evol Ecol Res 5, 43–51 (2003).
Hughes, K. A., Ott, S., Bölter, M. & Convey, P. Colonisation processes. In: Bergstrom, D. M., Convey, P., Huiskes, A. H. L (eds) Trends in Antarctic terrestrial and limnetic ecosystems: Antarctica as a global indicator. Springer, Dordrecht, pp 35–54 (2006).
Williamson, M. & Fitter, A. The varying success of invaders. Ecology 77, 1661–1666, https://doi.org/10.2307/2265769 (1996).
Frenot, Y. et al. Biological invasions in the Antarctic: extent, impacts and implications. Biol Rev 80, 45–72, https://doi.org/10.1017/S1464793104006542 (2005).
Stachowicz, J. J., Terwin, J. R., Whitlatch, R. B. & Osman, R. W. Linking climate change and biological invasions: Ocean warming facilitates nonindigenous species invasions. Proc Natl Acad Sci 99, 15497–15500, https://doi.org/10.1073/pnas.242437499 (2002).
Suttle, K. B., Thomsen, M. A. & Power, M. E. Species interactions reverse grassland responses to changing climate. Science 315, 640–642, https://doi.org/10.1126/science.1136401 (2007).
Vilà, M. et al. How well do we understand the impacts of alien species on ecosystem services? A pan-European, cross-taxa assessment. Front Ecol Environ 8, 135–144, https://doi.org/10.1890/080083 (2010).
Ward, N. L. & Masters, G. J. Linking climate change and species invasion: an illustration using insect herbivores. Glob Change Biol 13, 1605–1615, https://doi.org/10.1111/j.1365-2486.2007.01399.x (2007).
Frenot, Y., Gloaguen, J. & Trehen, P. Climate change in Kerguelen Islands and colonization of recently deglaciated areas by Poa kerguelensis and P. annua. In: Battaglia, B., Valencia, J., Walton, D. (eds) Antarctic communities: species, structure and survival. Cambridge University Press, Cambridge, pp 358–366
Ingimarsdóttir, M., Ripa, J., Magnúsdóttir, Ó. B. & Hedlund, K. Food web assembly in isolated habitats: A study from recently emerged nunataks, Iceland. Basic Appl Ecol 14, 174–183, https://doi.org/10.1016/j.baae.2012.12.002 (2013).
Smith, V. R. & Steenkamp, M. Climatic change and its ecological implications at a subantarctic island. Oecologia 85, 14–24, https://doi.org/10.1007/BF00317338 (1990).
Bergstrom, D. M. & Chown, S. L. Life at the front: history, ecology and change on Southern Ocean Islands. Trends Ecol Evol 14, 472–477, https://doi.org/10.1016/S0169-5347(99)01688-2 (1999).
Greve, M., Mathakutha, R., Steyn, C. & Chown, S. L. Terrestrial invasions on sub-Antarctic Marion and Prince Edward Islands. Bothalia 47, a2143, https://doi.org/10.4102/abc.v47i2.2143 (2017).
Lebouvier, M. et al. The significance of the sub-Antarctic Kerguelen Islands for the assessment of the vulnerability of native communities to climate change, alien insect invasions and plant viruses. Biol Invasions 13, 1195–1208, https://doi.org/10.1007/s10530-011-9946-5 (2011).
Laparie, M. & Renault, D. Physiological responses to temperature in Merizodus soledadinus (Col., Carabidae), a subpolar carabid beetle invading sub-Antarctic islands. Polar Biol 39, 35–45, https://doi.org/10.1007/s00300-014-1600-0 (2016).
Jeannel, R. Les Trechides de la Paléantarctide occidentale. In: Deboutteville, C. D. & Rapoport, E. (eds) Biologie de l’Amérique australe. Editions du CNRS, Paris, pp 527–655 (1962).
Roux, P. & Voisin, J. F. Notes sur les Carabiques des iles Falkland (Col. Caraboidea). Bull - Soc Entomol Fr 200–204 (1982).
Chevrier, M., Vernon, P., Frenot Y. Potential effects of two alien insects on a subantarctic wingless fly in the Kerguelen Islands. In: Battaglia, B., Valencia, J., Walton, D. W. H (eds) Antarctic communities: species, structure and survival. Cambridge University Press, Cambridge, pp 424–431 (1997).
Ouisse, T., Laparie, M., Lebouvier, M. & Renault, D. New insights into the ecology of Merizodus soledadinus, a predatory carabid beetle invading the sub-Antarctic Kerguelen Islands. Polar Biol 40, 2201–2209, https://doi.org/10.1007/s00300-017-2134-z (2017).
Chown, S. L., Gremmen, N. J. M. & Gaston, K. J. Ecological biogeography of Southern Ocean Islands: species‐area relationships, human impacts, and conservation. Am Nat 152, 562–575, https://doi.org/10.1086/286190 (1998).
Lalouette, L. et al. Thermal biology of the alien ground beetle Merizodus soledadinus introduced to the Kerguelen Islands. Polar Biol 35, 509–517, https://doi.org/10.1007/s00300-011-1096-9 (2012).
Ouisse, T. et al. The importance of relative humidity and trophic resources in governing ecological niche of the invasive carabid beetle Merizodus soledadinus in the Kerguelen archipelago. J Insect Physiol 93–94, 42–49, https://doi.org/10.1016/j.jinsphys.2016.08.006 (2016).
Renault, D. et al. Characterization of the habitats colonized by the alien ground beetle Merizodus soledadinus at the Kerguelen islands. Rev Ecol 70:28–32 (2015).
Leihy, R. I., Duffy, G. A., Nortje, E. & Chown, S. L. Data Descriptor: High resolution temperature data for ecological research and management on the Southern Ocean Islands. Scientific Data 5, 180177, https://doi.org/10.1038/sdata.2018.177 (2018).
Dillon, M. E., Frazier, M. R. & Dudley, R. Into thin air: physiology and evolution of alpine insects. Integr Comp Biol 46, 49–61, https://doi.org/10.1093/icb/icj007 (2006).
Jenkin, J. F. Macquarie Island, Subantarctic. In: Rosswall, T. & Heal, O. W. (eds) Structure and function of tundra ecosystems. Ecological Bulletins, Stockholm, pp 375–397 (1975)
Hugo-Coetzee, E. A. & Le Roux, P. C. Distribution of microarthropods across altitude and aspect in the sub-Antarctic: climate change implications for an isolated oceanic island. Acarologia 53, 43–60 (2018).
Hullé, M., Pannetier, D., Simon, J. C., Vernon, P. & Frenot, Y. Aphids of sub-Antarctic Iles Crozet and Kerguelen: species diversity, host range and spatial distribution. Antarctic Science 15, 203–209 (2003).
Davies, K. F., Melbourne, B. A., McClenahan, J. L. & Tuff, T. Statistical models for monitoring and predicting effects of climate change and invasion on the free-living insects and a spider from sub-Antarctic Heard Island. Polar Biol 34, 119–125 (2011).
Davies, K. F. & Melbourne, B. A. Statistical models of invertebrate distribution on Macquarie Island: a tool to assess climate change and local human impacts. Polar Biol 21, 240–250, https://doi.org/10.1007/s003000050359 (1999).
Gremmen, N. J. M., Chown, S. L. & Marshall, D. J. Impact of the introduced grass Agrostis stolonifera on vegetation and soil fauna communities at Marion Island, sub-Antarctic. Biol Conserv 85, 223–231, https://doi.org/10.1016/S0006-3207(97)00178-X (1998).
Mirth, C. K. & Riddiford, L. M. Size assessment and growth control: how adult size is determined in insects. BioEssays 29, 344–355, https://doi.org/10.1002/bies.20552 (2007).
Moczek, A. P. Horn polyphenism in the beetle Onthophagus taurus: larval diet quality and plasticity in parental investment determine adult body size and male horn morphology. Behav Ecol 9, 636–641, https://doi.org/10.1093/beheco/9.6.636 (1998).
Partridge, L. & French, V. Thermal evolution of ectotherm body size: why get big in the cold. In I., Johnston & A., Bennett (Eds.), Animals and Temperature: Phenotypic and Evolutionary Adaptation (Society for Experimental Biology Seminar Series, pp. 265–292). Cambridge University Press, https://doi.org/10.1017/CBO9780511721854.012 (1996).
Ciplak, B., Sirin, D., Taylan, M. S. & Kaya, S. Altitudinal size clines, species richness and population density: case studies in Orthoptera. J Orthoptera Res 17, 157–163, https://doi.org/10.1665/1082-6467-17.2.157 (2008).
Krasnov, B., Ward, D. & Shenbrot, G. Body size and leg length variation in several species of darkling beetles (Coleoptera: Tenebrionidae) along a rainfall and altitudinal gradient in the Negev Desert (Israel). J Arid Environ 34, 477–489, https://doi.org/10.1006/jare.1996.0126 (1996).
Sota, T. Altitudinal variation in life cycles of carabid beetles: life-cycle strategy and colonization in alpine zones. Arctic and Alpine Research 28, 441–447 (1996).
van der Have, T. M. & de Jong, G. Adult size in ectotherms: temperature effects on growth and differentiation. J Theor Biol 183, 329–340, https://doi.org/10.1006/jtbi.1996.0224 (1996).
O’Brien, D. M., Fogel, M. L. & Boggs, C. L. Renewable and nonrenewable resources: Amino acid turnover and allocation to reproduction in Lepidoptera. Proc Natl Acad Sci 99, 4413–4418, https://doi.org/10.1073/pnas.072346699 (2002).
Tigreros, N. Linking nutrition and sexual selection across life stages in a model butterfly system. Funct Ecol 27, 145–154, https://doi.org/10.1111/1365-2435.12006 (2013).
Wheeler, D. E., Tuchinskaya, I., Buck, N. A. & Tabashnik, B. E. Hexameric storage proteins during metamorphosis and egg production in the diamondback moth, Plutella xylostella (Lepidoptera). J Insect Physiol 46, 951–958, https://doi.org/10.1016/S0022-1910(99)00202-4 (2000).
Teets, N. M. & Denlinger, D. L. Physiological mechanisms of seasonal and rapid cold-hardening in insects. Physiol Entomol 38, 105–116, https://doi.org/10.1111/phen.12019 (2013).
Yancey, P. H. Organic osmolytes as compatible, metabolic and counteracting cytoprotectants in high osmolarity and other stresses. J Exp Biol 208, 2819–2830, https://doi.org/10.1242/jeb.01730 (2005).
Hidalgo, K. et al. Metabolic fingerprinting of the responses to salinity in the invasive ground beetle Merizodus soledadinus at the Kerguelen Islands. J Insect Physiol 59, 91–100, https://doi.org/10.1016/j.jinsphys.2012.10.017 (2013).
Colinet, H., Hance, T. & Vernon, P. Water relations, fat reserves, survival, and longevity of a cold-exposed parasitic wasp Aphidius colemani (Hymenoptera: Aphidiinae). Environ Entomol 35, 228–236, https://doi.org/10.1603/0046-225X-35.2.228 (2006).
Lalouette, L. et al. Cold exposure and associated metabolic changes in adult tropical beetles exposed to fluctuating thermal regimes. FEBS J 274, 1759–1767, https://doi.org/10.1111/j.1742-4658.2007.05723.x (2007).
Foray, V. et al. A handbook for uncovering the complete energetic budget in insects: the van Handel's method (1985) revisited. Physiol Entomol 37, 295–302, https://doi.org/10.1111/j.1365-3032.2012.00831.x (2012).
Laparie, M., Larvor, V., Frenot, Y. & Renault, D. Starvation resistance and effects of diet on energy reserves in a predatory ground beetle (Merizodus soledadinus; Carabidae) invading the Kerguelen Islands. Comp Biochem Physiol A Mol Integr Physiol 161, 122–129, https://doi.org/10.1016/j.cbpa.2011.09.011 (2012).
Bundy, J. G., Davey, M. P. & Viant, M. R. Environmental metabolomics: a critical review and future perspectives. Metabolomics 5, 3–21, https://doi.org/10.1007/s11306-008-0152-0 (2009).
Viant, M. R. Recent developments in environmental metabolomics. Mol Biosyst 4, 980, https://doi.org/10.1039/b805354e (2008).
Khodayari, S. et al. Deciphering the metabolic changes associated with diapause syndrome and cold acclimation in the two-spotted spider mite Tetranychus urticae. PloS ONE 8, e54025, https://doi.org/10.1371/journal.pone.0054025 (2013).
Mangor, K., Drønen, N. K., Kærgaard, K. H., Kristensen, S. E. Shoreline Management Guidelines. DHI, Hørsholm, Denmark, 450p (2017).
Robin, M., Chapuis, J. L. & Lebouvier, M. Remote sensing of vegetation cover change in islands of the Kerguelen archipelago. Polar Biol 34, 1689–1700 (2011).
Breheny, P., Burchett, W. visreg: Visualization ofregression models. R package version 2.3-0. https://CRAN.R-project.org/package=visreg.
Lê, S., Josse, J. & Husson, F. FactoMineR: an R package for multivariate analysis. J Stat Softw 25, 1–18, https://doi.org/10.18637/jss.v025.i01 (2008).
Venables, W. N. & Ripley, B. D. Random and mixed effects. In: Modern Applied Statistics with S. Springer, New York, pp 271–300 (2002).
R Core Team R: A language and environment for statistical computing. R Foundation for Statistical Computing, Vienna, Austria (2016).
The authors wish to thank Maxime Dahirel for statistical support and advice, and to the helpful French Polar Institute (IPEV) logistics team that greatly assisted field work. This research was supported by InEE-CNRS (Enviromics call, ‘ALIENS’; Zone Atelier Antarctique et Subantarctique), and the French Polar Institute (IPEV, program 136 ‘Subanteco’). Metabolic analyses were performed using the facilities from the PLAY platform (UMR CNRS Ecobio, Rennes, France). Peter Convey is supported by NERC core funding to the British Antarctic Survey's ‘Biodiversity, Evolution and Adaptation’ Team.
The authors declare no competing interests.
Publisher’s note Springer Nature remains neutral with regard to jurisdictional claims in published maps and institutional affiliations.
About this article
Cite this article
Ouisse, T., Day, E., Laville, L. et al. Effects of elevational range shift on the morphology and physiology of a carabid beetle invading the sub-Antarctic Kerguelen Islands. Sci Rep 10, 1234 (2020). https://doi.org/10.1038/s41598-020-57868-0
Scientific Reports (2020)