A generalist herbivore requires a wide array of plant species to maintain its populations
Introduction
For herbivorous insects, diet breadth plays an essential role in a range of ecological phenomena, such as population dynamics (Eskildsen et al., 2015; Descombes et al., 2016) and interspecific interactions (Carvalheiro et al., 2010; Charles and Linklater, 2013). The risk of extinction may also be related to diet breadth (Goulson et al., 2005). For example, the abundance of specialist herbivores decreases when the proportional abundance of their host plants in their habitat decreases (Jonsen and Fahrig, 1997; Steffan-Dewenter and Tscharntke, 2000; Rand and Tscharntke, 2007), and the loss of a host plant causes local extinctions of any specialist herbivores that depend on it (Uchida and Ushimaru, 2014). Thus, specialist herbivores are susceptible to changes in the plant community within their habitats. Conversely, the loss of potential host plants is less likely for generalist herbivores than for specialists because they can use a wide range of plant species. Therefore, the risk of extinction for generalist herbivores does not seem to be associated with changes in plant community composition; rather, declines in generalist herbivorous insects are widely accepted to be caused by such changes as the loss of suitable habitat (Thomas, 1985; Warren et al., 2001) and changes in vegetation structure (Gardiner et al., 2002; Hochkirch et al., 2008).
However, under certain circumstances the composition of the plant community in the habitat may even affect the fitness of generalist herbivores. For example, similarly to specialist herbivores, a population of generalist herbivores cannot persist if the overall abundance of host plants in its habitat is low (i.e., the herbivore is relatively oligophagous). In other cases, an array of plant species might be important to a generalist's population persistence. Indeed, some generalist herbivores show a preference for certain host plants, although they can potentially consume a wide range of plant species (Ibanez et al., 2013; Huang et al., 2016). If maturation and/or reproduction is constrained by the shortage of some nutrients, a potentially generalist herbivore should still prefer the host plants that include such essential nutrients. Growth and reproduction can be controlled by controlling the balance among different nutrients consumed (Raubenheimer and Simpson, 1993; Bernays et al., 1994; Lee et al., 2008; Behmer and Joern, 2008; Behmer, 2009; Franzke et al., 2010; Polak et al., 2017), so the extinction risk of generalist herbivores may be increased not only by the loss of habitat, but also by changes in their habitats' plant communities. Therefore, to evaluate habitat quality for the effective conservation of threatened generalist herbivores it is essential to know exactly what plants the herbivore eats.
Decreases in populations of Celes akitanus (Orthoptera: Acrididae), which is considered a generalist grasshopper, might be associated with plant community changes. Populations of C. akitanus were distributed across central and northern Honshu, Japan, until the early 20th century (e.g., Uchida et al., 2016a), but at present only a few populations are known to exist in distantly separated localities. An intensive investigation of the plant and insect communities of one of the localities with extant populations (in Nagano Prefecture) revealed that C. akitanus has survived in only a few specific types of grasslands (Uchida et al., 2016a). In that locality, grasslands are subjected to four types of management (traditional, burning, mowing, and abandonment; see Materials and methods for details), and C. akitanus is found exclusively in grasslands subjected to one of these, specifically traditional management (hereinafter referred to as traditional grasslands). Given that in other localities this grasshopper species also occurs in grasslands subjected only to burning or mowing management, as well as in seaside natural grasslands (Nagahata, 2006; Okatsu et al., 2018; Uchida, unpublished data), it seems unlikely that differences in management practices are the direct cause of its exclusive occurrence in traditional grasslands in Nagano. However, grassland plant communities vary depending on management practices, and the traditional grasslands harbour plant communities of higher species richness than those in other types of grasslands. We therefore hypothesized that the characteristics of plant communities mediate the persistence of C. akitanus populations; this could be, for example, because certain host plants exist exclusively in traditional grasslands, or because the grasshopper may need to inhabit a community with high plant species richness to meet some of its physiological or life history requirements (e.g., to control the balance of nutrients).
In the present study, we examined the abundance of C. akitanus in various grasslands to explore the relationship between this grasshopper and plant species composition. In addition, to empirically assess whether this grasshopper is a generalist we determined its host plant species and the frequency of feeding on each host plant using DNA barcoding of its faeces. Based on these results, we discussed the hypothesis that the persistence of C. akitanus populations is associated with host plant composition in semi-natural grasslands.
Section snippets
Study sites
We investigated the abundance of C. akitanus and the composition of the plant community in 12 semi-natural grasslands occurring close to one other within a relatively small area (~7150 ha) in central Nagano Prefecture, Japan (Fig. 1). Because C. akitanus is a highly threatened species that is protected by the local government, we do not specify the exact locations of our study sites herein. We examined 36 plots (each 5 × 30 m) in 12 grasslands under different management practices: traditional,
C. akitanus and plant community surveys
We found 4, 35, and 29 individuals of C. akitanus in 2013, 2014, and 2015 respectively. These 68 individuals were found in six of the 14 survey rounds conducted, and exclusively in traditional grasslands. In 2014 and 2015, faeces were obtained from 26 of the collected individuals by retaining them in separate 50 mL-tubes; 20 individuals were collected in the traditional grasslands investigated in the present study and the others six were collected outside of our studied grasslands.
In the plant
Discussion
Our results suggested that C. akitanus abundance depends on the specific composition of the plants available in its habitat. We demonstrated that C. akitanus is a generalist herbivore, as this species was able to consume a wide range of plant species (i.e., at least 36 plant species assigned to 19 families; Table S1; Fig. 2). Although this grasshopper showed a preference for a subset of plants (i.e., 10 host plant species were suggested to be eaten more than expected by random chance), these
Authors' contributions
K.U. and S.Y. designed the study. S.Y. conducted molecular work and metabarcoding analysis. K.U. conducted field surveillance and data analysis. Both authors wrote the manuscript.
Acknowledgements
We thank Yuko Nagata, Sogo Takahashi, Tadashi Shinohara, Naoyuki Nakahama, Atushi Ushimaru, Yasuoki Takami, Takeshi Suka, and Masayoshi Nasuno. Those people helped our fieldwork and gave many advices. This study was partially supported by the Grant-in-aid for JSPS Research Fellow No. 13J03127, Zoshinkai Fund for Protection of Endangered Animals, and Nippon Life Insurance Foundation to K.U., and JSPS KAKENHI Grant No. 14444453 to S.Y.
Competing interests
We declare we have no competing interests.
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These authors contributed equally to this work.