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Review

Phylogeography of Phytophagous Weevils and Plant Species in Broadleaved Evergreen Forests: A Congruent Genetic Gap between Western and Eastern Parts of Japan

1
Graduate School of Human and Environmental Studies, Kyoto University, Kyoto, Kyoto 606-8501, Japan
2
Makino Herbarium, Tokyo Metropolitan University, Hachioji, Tokyo 192-0397, Japan
*
Author to whom correspondence should be addressed.
Insects 2011, 2(2), 128-150; https://doi.org/10.3390/insects2020128
Submission received: 28 February 2011 / Accepted: 15 April 2011 / Published: 21 April 2011
(This article belongs to the Special Issue Phylogeographic Syntheses)

Abstract

: The Quaternary climate cycles played an important role in shaping the distribution of biodiversity among current populations, even in warm-temperate zones, where land was not covered by ice sheets. We focused on the Castanopsis-type broadleaved evergreen forest community in Japan, which characterizes the biodiversity and endemism of the warm-temperate zone. A comparison of the phylogeographic patterns of three types of phytophagous weevils associated with Castanopsis (a host-specific seed predator, a generalist seed predator, and a host-specific leaf miner) and several other plant species inhabiting the forests revealed largely congruent patterns of genetic differentiation between western and eastern parts of the main islands of Japan. A genetic gap was detected in the Kii Peninsula to Chugoku-Shikoku region, around the Seto Inland Sea. The patterns of western-eastern differentiation suggest past fragmentation of broadleaved evergreen forests into at least two separate refugia consisting of the southern parts of Kyushu to Shikoku and of Kii to Boso Peninsula. Moreover, the congruent phylogeographic patterns observed in Castanopsis and the phytophagous insect species imply that the plant-herbivore relationship has been largely maintained since the last glacial periods. These results reinforce the robustness of the deduced glacial and postglacial histories of Castanopsis-associated organisms.

1. Introduction

Phylogeographic patterns of extant genetic variation in organisms have proven to be highly informative in recovering their postglacial demographic histories [1,2]. Another powerful method is comparing the intraspecific phylogeographic patterns among several taxa over the same area and searching for congruent geographic patterns of genetic variation, which indicate the influence of common historical factors [316]. Comparing the intraspecific phylogeographic patterns among different species distributed within a single vegetation zone should be more informative because a group of species living together in the present environment are likely to have responded similarly to past geological and climatic events [3,17]. In the present study, we focused on the broadleaved evergreen forest community in Japan that characterizes the biodiversity and endemism of the warm temperate zone.

Climatic changes during glacial periods have had a major influence on the recent evolutionary history of living organisms, even in the warm-temperate zone, where land was not covered by ice sheets [18,19]. The geological and geographical features of the Japanese Archipelago consist of several mountain ranges running parallel to a northeast-southwest-oriented axis. As the coastal belt is close to these mountain ranges, the climate varies even within a narrow region. Consequently, various types of vegetation occur in the archipelago (Figure 1a). Moreover, several landbridges between Japan and its surrounding areas, which formed or disappeared in response to glacial-interglacial climatic changes, have played important roles in determining the current distribution of the biological diversity in Japan [20]. Current warm-temperate and subtropical zones in the Japanese Archipelago are covered with forests mainly dominated by three types of broadleaved evergreen trees: Castanopsis, Quercus, and Machilus [21].

Palynological evidence indicates that broadleaved evergreen forests in Japan were subjected to cold periods at least four times during the Quaternary [18,19]. Throughout the glacial periods, climatic cooling caused southward and toward lower altitudes shifts in the geographic distribution of these forests. The pollen record indicates that refugial populations of broadleaved evergreen forests were restricted to southern areas, mainly at the southern end of Kyushu, and migrated northward from the refugia after the Last Glacial Maximum (LGM) (see Figure 1b,c and [19,22,23]).

In this study, we used molecular markers to compare the intraspecific phylogeographic patterns of several plant and insect species present in a Japanese Castanopsis-type broadleaved evergreen forest community. Plant chloroplast DNA (cpDNA) is effectively haploid with a small effective population size and is usually maternally inherited and thus often used in molecular phylogeographic studies. However, the molecular evolutionary rate of cpDNA has been reported to be relatively slow at the nucleotide sequence level [2426]. We first surveyed the intraspecific variation among many component species of broadleaved evergreen forests using nucleotide sequence analyses of cpDNA. We aimed to identify the species that had a relatively large incidence of intraspecific cpDNA variation [27,28]. Eight species growing in Castanopsis-dominant forests were selected for the phylogeographic study. Furthermore, we used microsatellite markers (expressed sequence tags-simple sequence repeat: EST-SSR) from Castanopsis owing to its extremely low levels of intraspecific variation in cpDNA.

Castanopsis trees are associated with diverse herbivorous insects. We investigated phylogeographic patterns based on the current geographic distribution of the informative mitochondrial DNA (mtDNA) diversity among three types of the weevils associated with Castanopsis: the host-specific seed-boring weevil Curculio hilgendorfi, the generalist seed-boring weevil Curculio sikkimensis, and the host-specific leaf-mining weevil Rhynchaenus dorsoplanatus. The phytophagous beetle species has an advantage of low dispersability, e.g., only flying to oviposition substrates (i.e., seeds and new leaves). Moreover, these almost flightless and nonmigratory insects likely responded to environmental changes associated with the glacial cycles in a manner similar to their host plants. Thus, we compared the genetic structures of these weevils with those of Castanopsis. If the plant-insect association (i.e., the host range of the weevil) remained stable throughout the Quaternary, the presence of the phytophagous insects may be an indicator of the coverage of the associated forests. Thus, incorporating phylogeographic information of phytophagous insect species into that of the host plant species could elucidate more precisely the phylogeographic patterns of the inhabited forests.

In this paper, we reviewed and compared the phylogeographic patterns of plant and insect species inhabiting the Castanopsis-type broadleaved evergreen forests in Japan. This study addressed whether geographic patterns of genetic variation are congruent between the plant species growing in Castanopsis-type forests and whether phylogeographic patterns are similar among the host plants Castanopsis and the three types of the weevil species that share the same host. The phylogeographic patterns of these weevil species will enable us to reconstruct the glacial and postglacial history of the associated Castanopsis forests in Japan.

2. Experimental Section

2.1. Plant Species

We first surveyed the intraspecific variation among 61 component species of broadleaved evergreen forests in Japan and the surrounding areas using the nucleotide sequence analyses of cpDNA. Among these species, intraspecific cpDNA variation was detected in 17 plant species. We selected eight species belonging to distantly related plant families that inhabit Castanopsis-dominant forests.

Seven species out of the eight plant species, such as Elaeocarpus sylvestris var. ellipticus, Prunus zippeliana, Myrsine seguinii, Daphne kiusiana, Alpinia japonica, Arachniodes sporadosora, and Arachniodes aristata, have a similar geographic distribution pattern (along the Pacific coast up to the Boso Peninsula, known as the northern limit of the distribution), but represent a diverse array of life histories (i.e., ferns, perennials, shrubs, and trees) and dispersal modes (i.e., wind and birds) (Table 1). Our sampling sites covered practically the entire range of distribution of these plant species throughout Japan. The current geographic distribution of Photinia glabra is different from those of the above-mentioned species, occurring primarily in Kinki and the eastern Shikoku and Chugoku regions. Disjunct populations are known in the Amakusa Islands of southwestern Kyushu. Sequencing of noncoding regions of cpDNA and data analyses are described in previous research cited in Table 1.

We investigated the phylogeographic patterns of Castanopsis by analyzing EST-SSR markers [3841]. The plant genus Castanopsis in Japan consists of two species, Ca. cuspidata and Ca. sieboldii, and the latter is divided into two varieties, var. sieboldii and var. lutchuensis [42,43]. Castanopsis cuspidata and Ca. sieboldii var. sieboldii are distributed among the main islands of Japan and Ca. sieboldii var. lutchuensis is only found within the Ryukyu Islands. Castanopsis cuspidata and Ca. sieboldii var. sieboldii are sometimes distributed sympatrically in the main islands and can be morphologically distinguished by differences in their seed size, shape, and the structure of their leaf epidermis [42,44]. Castanopsis sieboldii var. sieboldii has large oblong seeds and exhibits two epidermis cell layers, whereas Ca. cuspidata has small globular seeds and one epidermis cell layer. Intermediate morphological types have been frequently reported, especially at sites where the two species coexist [45,46]. EST-SSR analyses based on Ueno et al. [38] were performed and an unweighted pair group method with arithmetic mean (UPGMA) dendrogram was constructed based on Nei's genetic distance [47].

2.2. Insect Species

We investigated the genetic variation in mtDNA of three types of weevils (Coleoptera: Curculionidae): C. hilgendorfi, C. sikkimensis, and R. dorsoplanatus, which are associated with Castanopsis trees. Curculio hilgendorfi is an obligate seed predator whose larvae feed specifically on the seeds of Ca. sieboldii in Japan, whereas C. sikkimensis is a generalist seed predator associated with deciduous and evergreen Fagaceae trees [i.e., Quercus (deciduous and evergreen), Lithocarpus (evergreen), Castanopsis (evergreen), and Castanea (deciduous)]. Rhynchaenus dorsoplanatus is a host-specific leaf miner of Castanopsis (i.e., Ca. sieboldii var. sieboldii and Ca. cuspidata).

The female Curculio drills into Castanopsis seeds with extremely long rostra and oviposits in the pore during autumn. The larvae feed on the seeds prior to being left to overwinter in the soil, pupating before they emerge in spring or summer. New Castanopsis leaves are bored by female Rhynchaenus with their short rostra and oviposit in the perforation during spring. Palisade and spongy parenchyma of the leaves are consumed by the larvae. In late spring, adult weevils emerge from the leaves. Our sampling sites covered practically the entire range of distribution of these weevil species throughout Japan. Sequencing of mtDNA and data analyses are described in previous research cited in Table 1.

3. Results and Discussion

3.1. Common Phylogeographic Patterns among the Broadleaved Evergreen Plant Species

Genetic structure

The geographic distribution patterns of cpDNA haplotypes from several broadleaved evergreen species showed no clear geographical structuring (Table 1). The molecular evolutionary rate of cpDNA has been reported to be relatively slow at the nucleotide sequence level [2426]. In fact, the molecular evolutionary rate of noncoding cpDNA regions (trnT-trnL, trnL-trnF, atpB-rbcL, rps16, trnG, psbC-trnS, trnG-trnfM, trnW-trnP, petB, petD-rpoA, rpl16) that are often used for phylogeographic analyses is also slow, i.e., 1.2 × 10−10 (including indels) and 7.7 × 10−11 (nucleotide substitutions only) substitutions per site per year [32], or one nucleotide substitution every two million years per site on average. In general, relatively low levels of cpDNA variation are usually found within species. Moreover, extremely low levels of intraspecific variation in cpDNA were reported in Japanese broadleaved evergreen species [27,28] than in plants growing in other vegetation zones, i.e., broadleaved deciduous species [48] and alpine species [49]. This result suggests that the effects of climate change are particularly severe for members of the broadleaved evergreen forests community in the warm-temperate zone. Nevertheless, the geographic distribution patterns of cpDNA haplotypes in several plant species (Table 1, Figure 2a,c,d) and the clusters found among the EST-SSR variation of Ca. sieboldii (Figure 2e) clearly differentiated populations between the western and eastern parts of the main islands of Japan. Moreover, P. zippeliana (Figure 2b) and Ca. sieboldii (Figure 2e) showed genetic uniqueness in the Ryukyu Islands. This apparent geographical structuring was observed in the tree species, especially in the dominant species, rather than in herbs or ferns.

Genetic uniqueness and genetic diversity

We compared the intraspecific phylogeographic patterns among six plant species (P. zippeliana, A. japonica, D. kiusiana, E. sylvestris var. ellipticus, A. sporadosora, and A. aristata; see Table 1 for materials) inhabiting the broadleaved evergreen forests with respect to cpDNA haplotype uniqueness and haplotype diversity [3]. Many rare haplotypes and the greatest numbers of haplotypes were observed in the Ryukyu Islands and Kyushu, a finding that agreed with fossilized pollen data demonstrating the past existence of refugia in the Ryukyu Islands [30] and southern Kyushu (see Figure 1b and [19,22]).

Note that several rare types were observed on the Muroto Peninsula and that the number of common haplotypes was also high on the Kii Peninsula. Because the Muroto Peninsula was contiguous with the Kii Peninsula during the LGM (see Figure 1b and [19,29]), we also hypothesized that additional important refugia existed from the Muroto to Kii peninsulas during the glacial periods, where pollen records of broadleaved evergreen species are scarce. Moreover, the phylogeographic pattern of cpDNA in P. glabra with a current disjunctive geographic distribution also supports the existence of the two refugia of southern Kyushu and around the Kii Peninsula [35].

With regard to the relatively slow rate in molecular evolution of cpDNA discussed above, most of the cpDNA haplotypes found in one plant species probably originated long before the Quaternary period. The geographic distribution of most Japanese broadleaved evergreen species was probably restricted to the two refugia of the western and eastern parts during repeated glacial periods in the Quaternary period. After climate warming, since the LGM about 20,000 years ago, these surviving populations may have expanded very slowly and have not come into contact with some species as of yet.

3.2. Common Phylogeographic Patterns among Host Plant Castanopsis and the Weevil Species

Genetic structure

A comparison of the genetic structures between the host plant and insects revealed that the patterns of genetic differentiation are largely congruent in the western and eastern parts of the main islands. Moreover, congruent phylogeographic patterns were observed among the three weevils (see Figure 1f–h and [33,34,36]), with a gap between the western and eastern clades on the main islands with respect to the mtDNA sequences. The observed gap between the western and eastern clades of these weevils suggests that the western and eastern insect populations have been isolated for a long time, probably through several glacial and interglacial periods; the genetic groups have not been in contact for several thousands of years since the last glacial period, and long-distance migration of the weevil has been rare, resulting in negligible interpopulation genetic exchange events. This result suggests past fragmentation of these weevils into at least two separate regions. Among these weevils, only C. hilgendorfi is distributed in the Ryukyu Islands. The phylogenetic tree and haplotype network of C. hilgendorfi showed that Ryukyu populations have clearly differentiated genetically from those of the main islands of Japan (see Figure 2f and [33]), which is also demonstrated by the patterns of the host plant Ca. sieboldii (Figure 2e).

The broad-scale congruent phylogeographic pattern of western and eastern separation in the main islands observed among the weevils suggests that they experienced similar historical and environmental changes. Some differences in the patterns were also observed among these species. A larger gap of the western and eastern clades and a higher genetic differentiation between these areas were observed in C. hilgendorfi, whereas low genetic differentiation between the clades and the existence of several clades in the intermediate areas of Chugoku-Shikoku were detected in C. sikkimensis and R dorsoplanatus. Moreover, genetic differentiation was noted in the western clade of C. hilgendorfi between the coasts of the Pacific and the Sea of Japan, which suggested the existence of additional important refugia in the northwest part of Kyushu in addition to the southern end of Kyushu.

These distinctions in the extent of the genetic differentiation may have been affected by differences in host specificity and plant parts infested by weevil species, jointly with flight ability and differences in life history. Among these weevil species, C. hilgendorfi has the strongest host specificity (i.e., one-to-one association). The lack of distribution of the host plant Ca. sieboldii around the Seto Inland Sea may have prompted genetic differentiation between C. hilgendorfi on the Pacific coast and those on the coast of the Sea of Japan. In contrast, C. sikkimensis is a generalist seed predator of Fagaceae plants and could migrate across the Seto Inland Sea using several of these plant species in the Chugoku-Shikoku regions. This polyphagous habit allowed C. sikkimensis to cross the Seto Inland Sea and may have generated intermediate clades in the Chugoku-Shikoku region.

The weight of the leaf miner R. dorsoplanatus is about one-tenth that of C. hilgendorfi, and consequently, the former might have been transported by scarce strong winds such as a typhoon. Dispersal of larvae through the drifting of seeds or leaves containing the larvae is not likely to occur in either species. If gene flow in R. dorsoplanatus occasionally occurred by long-distance dispersal among isolated populations in the glacial refugia, the genetic differentiation between isolated refugia was not promoted. Weak genetic differentiation in R. dorsoplanatus may be explained by dispersion due to its small body size.

The seed-boring Curculio overwinters underground during its larval stage and has greater cold tolerance than R. dorsoplanatus, which overwinters at the stage of imago on the ground. Cold tolerance may have enabled Curculio to survive in isolated populations for a long time, probably through several glacial and interglacial periods, and consequently, it shaped the large genetic gap between the western and eastern clades. In addition, seeds are a more unpredictable resource than new leaves because the number of seeds available for predation greatly fluctuates annually and supra-annually [50,51]. For example, during a poor crop year, the population size of Curculio must have been gravely reduced, resulting in a population bottleneck. These ecological characteristics of the seed-parasitic weevil species may have caused stronger genetic structuring than in the leaf-mining weevil species.

The results suggested that broad-scale concordance of the phylogeographic patterns may have been formed by the common historical and environmental changes experienced by the weevils, whereas the local-scale discordance may have occurred by differences in the host specificity and ecological characteristics of the weevils. A more detailed explanation of what formed the local variations in these patterns can be estimated by comparing them to various phytophagous insects with diverse geographic distributions and life histories associated with Castanopsis.

Demography

We compared the demographic history of the two host-specific weevil associated with Castanopsis, C. hilgendorfi and R. dorsoplanatus. The expansion events of both weevil species in the main islands were dated approximately to 40,000–100,000 and 30,000–120,000 years ago, inferred from the mismatch distributions and coalescent-based Bayesian skyline plots, respectively [36]. Molecular dating based on a single locus should obviously be interpreted with caution. Nevertheless, these data suggested that the beginning time of these expansion events is consistent with the last glacial periods (120,000–12,000 years ago, [52]), when it was cooler than at present. The congruent time of the population expansion events of the two host-specific predators suggest that the associated Castanopsis forests experienced a reduction in population size during the last cooling. In C. hilgendorfi, large sequence diversity and multimodal mismatch distribution of sequence differences in the Ryukyu Islands populations were observed [33]. This suggests that historically, these populations have been large enough for ancestral polymorphism to be retained for a long time.

3.3. Glacial and Postglacial History of Broadleaved Evergreen Forests

Genetic uniqueness and higher genetic diversity observed in the Ryukyu Islands

The phylogeographic patterns of several plant species and C. hilgendorfi showed that populations found in the Ryukyu Islands have genetically differentiated from those of the main islands of Japan. Many rare haplotypes and the greatest numbers of haplotypes among plant species were observed in the Ryukyu Islands, although unique haplotypes were not detected in some plant species. Such genetic uniqueness and high genetic diversity were also found in several plant [10,53] and animal [54,55] species cohabiting in warm-temperate and subtropical zones in Japan. The Ryukyu Islands have been isolated from Kyushu since 1,500,000 years ago [56]. The genetic differentiation observed in these islands is suggested to be promoted by the long-term restriction of gene flow from the main islands. Indeed, the pollen records indicate the existence of broadleaved evergreen trees at the LGM in the Ryukyu Islands (see Figure 1b and [30]).

The large sequence diversity and demographic equilibrium in C. hilgendorfi suggest that the Ryukyu Islands populations have not experienced a rapid range expansion or serial population bottleneck during recent glacial periods. On these islands, insects associated with broadleaved evergreen forest trees could probably have survived in large populations throughout the entire duration of the glacial periods based on their location far to the south, which had a much warmer climate than that of the main islands.

Genetic differentiation between the western and eastern parts of the main islands

The genetic differentiation between the western and eastern populations observed among many plant and insect species in Castanopsis-type broadleaved evergreen forests suggests that the forests have been isolated from the western and eastern populations for an extended time, probably through several glacial and interglacial periods. Such a boundary is also found in several other plant species growing in warm-temperate zones in Japan (Table 2).

In Europe, the Alps and Pyrenees may have blocked the dispersal of many animal and tree species from Italian and Iberian refugia to the northern part of Europe (reviewed in [8,15]). However, in the case of the geographical boundary in the Chugoku-Shikoku region, neither a north-south mountain range nor a temperature gap has been observed. Other geographical and climatic features of the Seto Inland Sea, such as a currently drier climate and limited onshore wind, and the historical existence of a grassland landscape during dry cool climates in the glacial ages may have served as barriers against recolonization of various species from their refugia. The appearance of the inland sea between the Kii Peninsula and Shikoku region after the glacial periods has also served as barriers against recolonization from their refugia.

The following scenarios were deduced from these data: Japanese broadleaved evergreen forests in the mainland survived in the western, probably at the south end and northwestern part of Kyushu (from the data of C. hilgendorfi described in Section 3.2), and the eastern (probably around the Kii Peninsula from the data of several plants described in Section 3.1) parts during the last glacial period; and after climate warming, these surviving small forests may have expanded very rapidly along the coast from west to east.

In this study, C. sikkimensis inhabiting both broadleaved deciduous and evergreen forests and C. hilgendorfi associated only in broadleaved evergreen forests with several other plant species, shared a common phylogeographic pattern with both exhibiting a genetic gap between the eastern and western parts of Japan (Figure 2f,g). The geographic distributions of the genetic diversity of plant species and their parasitic insects suggest that both were restricted to separate western and eastern refugia on the main islands of Japan during repeated glacial periods in the Quaternary. Moreover, the geographical boundary in the Kii Peninsula (Kinki) to the Chugoku-Shikoku region was also observed in several other plant and animal species from warm- and cool-temperate zones of Japan (Table 2).

At the LGM, the global sea level is estimated to have dropped to about 140 m lower than the present level [80]. The narrowing of the Tsushima Strait at that time caused a reduction in the Tsushima Warm Current into the Sea of Japan, resulting in further cooling and the aridification of the Japanese Archipelago. Given this cool and arid climate, the areas covered by coniferous forests and cool-mixed forests expanded southward [81]. This suggests that both deciduous and evergreen forests were restricted to adjacent refugia at that time. The coincident patterns of C. sikkimensis and C. hilgendorfi strongly support the hypothesis that both deciduous and evergreen forest types survived together or adjacent to one another in small refugia during the glacial ages, although these forests are presently separately distributed in cool- and warm-temperate zones, respectively. The geographical boundary observed by many phylogeographic studies on the species in cool-temperate zones appears farther east of that of the species in warm-temperate zones. For example, the Chubu boundary was observed in many species from cool-temperate zones, whereas the Chugoku-Shikoku boundary was observed in many species from warm-temperate zones (Tables 1,2). A more detailed history can be estimated by comparing the phylogeographic patterns of various organisms with diverse life histories in these types of forests.

In some insect species from Japanese cool- and warm-temperate forests, the pattern of west-east differentiation has not been observed. For example, with regard to species interaction, the offensive trait of the weevil and the defensive trait of the plant are involved in a geographically structured arms race, suggesting the overwhelming strength of coevolutionary selection against the effect of historical events that may have limited local adaptation [82]. The divergence of flightless ground beetles (Ohomopterus) is suggested to have occurred with the varying fragmentation of favorable habitats by geographical barriers, evolution of body size, and genital morphology in local populations, and secondary contact and interactions between diverging populations [83]. The larvae of the beetle are specialized predators of megascolecid earthworms, and Ohomopterus populations depend on the presence of these earthworms. This non-phytophagous species appears to have its own distinctive evolutionary history, and the effects of historical climatic change at the vegetation scale were not significant on their present geographical distribution. Our data suggest that the continual historical change of the environment on Japanese broadleaved evergreen forests has contributed to shaping the recent genetic structure of phytophagous insects.

3.4. Phytophagous Insects Reveal Recent Evolutionary Histories of Their Host Plants

Whiteman and Parker [84] and Nieberding and Olivieri [85] summarized the theoretical framework for using parasites as proxies for their host evolutionary history. Parasites are most useful to complement host genealogy when host genetic data retain excessive ancestral polymorphisms or lack of population structure (e.g., species with low genetic variability owing to recent strong bottlenecks, endangered species, or invasive species [85]). Moreover, parasites with short generation times and high mutation rates, such as viruses, are most informative for deciphering recent host demographic events, because they can accumulate sufficient mutations in the short time periods [86].

Most plant species are associated with diverse host-specific phytophagous insects. In the case of a pair of the host plants and their host-specific phytophagous insects, the synonymous rate of sequence change has been estimated to be considerably faster in animal mtDNA than in plant cpDNA, mtDNA, or even nuclear DNA [26,8789]. With their shorter generation times and more quickly evolving genomes, phytophagous insects can be extremely useful tools for clarifying previously undetected historical events of their host plant. To apply genetic information of insects to their host plants, the phytophagous insects should be highly likely to have shared a common history with its host and to display a more resolved genetic pattern.

At the phylogenetic scale, several studies suggest that co-divergence of host plants and obligate pollination mutualistic insects have occurred [9092]. Several tests for analyzing the level of co-speciation between phylogenies indicate that a greater degree of correlation generally exists between host trees and their seed-parasitic pollinator phylogenies than expected from a random association [91].

At the intraspecific level, very few studies have compared the phylogeographic patterns or genealogies between plant species and their specialized herbivorous insect species. An alpine plant species and its specialized herbivorous insect, the butterfly, from the Rocky Mountains suggest that they respond similarly, but independently to climate cycles [93]. Incongruent patterns of genetic variation and independent biogeographic histories in the specialized plant-insect association suggest that by promoting habitat expansion and mixing among alpine populations, glacial periods repeatedly reset the distributions of genetic variation in each species and inhibited continual co-divergence among pairs of interacting species. The similar host and parasite genealogical tree has been scarcely observed in the specialized plant-insect association. In contrast, in the case of host-parasite relationships, partial spatial and temporal congruences in the differentiation of both field mice and their specific parasites (nematodes) were revealed [94]. The lack of or low levels of intraspecific variation in plants and high dispersability of insect species by flying may prevent the detailed phylogeographic congruence between plants and insects.

Parasite features shown to determine the strong likelihood of a parasite sharing a common history with its host are the level of intimacy of the interaction between the two organisms: host specificity, the lack of intermediate host and a free-living phase, or mutualistic symbionts [8486]. The existence of a free-flying phase in the imaginal stage might decrease the dependence of the insects on its host plants, even though insect species have high host-specificity. Subsequently, the assumption of intimate host-parasite relationships seems more difficult to demonstrate with phytophagous insects than with parasites. We should then select host-specific phytophagous insect species for the biogeographic study of host plants, such as almost flightless and nonmigratory or with a shorter imaginal stage.

Our study suggests that the geographic patterns of the genetic differentiation between western and eastern parts of the main islands are largely congruent between the host plant and its phytophagous insects. We could not directly compare the genealogical trees of the insects to its host plant because we did not perform the population analysis of the insect mtDNA variations. If the genealogical trees of the host plant and phytophyagous insects are identical in future studies, their comparisons suggest parallel histories of Castanopsis and its phytophagous insect populations during and after the last glacial periods. The investigation of recent phylogeographic processes directly from plant species that infer the historical dynamics, locate glacial refugia in the Quaternary, and reveal detailed postglacial colonizing routes has been somewhat limited due to the relatively slow rate in molecular evolution of cpDNA in plants and extremely low levels of intraspecific variation in cpDNA of Japanese broadleaved evergreen species. The use of DNA markers from insects with a faster evolutionary rate can make possible the reconstruction of previously undetected evolutionary and demographic histories of their host plants and associated forests. Indeed, analyses of C. hilgendorfi detected another refugial area (i.e., northwestern part of Kyushu) that was not previously recognized by analyzing intraspecific cpDNA variation of several plant species inhabiting the Castanopsis-type broadleaved evergreen forests (described in Section 3.2 and [33]). The congruent phylogeographic patterns that were observed in the weevil species reinforce the robustness of the deduced glacial and postglacial histories of Castanopsis-associated organisms.

4. Conclusions

Our data suggest that geological and historical environments have contributed to shaping the recent genetic structure of many plant and insect species inhabiting Castanopsis-type broadleaved evergreen forests of Japan. Comparing phylogeographic patterns of three types of phytophagous weevils (i.e., a host-specific seed predator, a generalist seed predator, and a host-specific leaf miner), and of several plant species, enabled us to specify the historical processes of these forests more precisely. We demonstrated that these insects and their host plant were restricted to separate western and eastern refugia on the main islands of Japan during repeated glacial periods in the Quaternary. The congruent phylogeographic patterns that were observed in the weevil species associated with the same host plant reinforce the robustness of the deduced glacial and postglacial histories of Castanopsis-associated organisms. Our analyses provide a foundation for exploring the evolutionary history of Japanese broadleaved evergreen forests, which characterize the biodiversity and endemism of the cool- and warm-temperate zones severely affected by climate change.

Figure 1. The location and vegetation of Japan. (a) The location of the Japanese Archipelago. The dotted line indicates the coastline of the Last Glacial Maximum about 20,000 years ago. (b) Vegetation during LGM based on Kamei and Research Group for the biogeography from Würm Glacial [29]. Circles indicate the existence of pollen records of broadleaved evergreen trees at the LGM [22,30]. (c) Potential natural vegetation at present [31].
Figure 1. The location and vegetation of Japan. (a) The location of the Japanese Archipelago. The dotted line indicates the coastline of the Last Glacial Maximum about 20,000 years ago. (b) Vegetation during LGM based on Kamei and Research Group for the biogeography from Würm Glacial [29]. Circles indicate the existence of pollen records of broadleaved evergreen trees at the LGM [22,30]. (c) Potential natural vegetation at present [31].
Insects 02 00128f1a 1024Insects 02 00128f1b 1024
Figure 2. The western-eastern differentiated pattern observed in the main islands of Japan. Many plants and insects inhabiting Castanopsis-type broadleaved evergreen forests share this pattern with a major phylogeographic break typically occurring at various points in the Kii Peninsula to Chugoku-Shikoku region around the Seto Inland Sea (modified from references shown in Table 1). (a–d) Geographic distribution of cpDNA haplotypes found among four plant species of broadleaved evergreen trees. (e) Geographic distribution of the UPGMA clusters found among EST-SSR markers of Ca. sieboldii, the dominant tree. (f–h) Geographic distribution of mtDNA clades found among three weevil species associated with Castanopsis.
Figure 2. The western-eastern differentiated pattern observed in the main islands of Japan. Many plants and insects inhabiting Castanopsis-type broadleaved evergreen forests share this pattern with a major phylogeographic break typically occurring at various points in the Kii Peninsula to Chugoku-Shikoku region around the Seto Inland Sea (modified from references shown in Table 1). (a–d) Geographic distribution of cpDNA haplotypes found among four plant species of broadleaved evergreen trees. (e) Geographic distribution of the UPGMA clusters found among EST-SSR markers of Ca. sieboldii, the dominant tree. (f–h) Geographic distribution of mtDNA clades found among three weevil species associated with Castanopsis.
Insects 02 00128f2a 1024Insects 02 00128f2b 1024
Table 1. Population studies based on genetic markers from plant and insect species inhabiting Japanese Castanopsis-type broadleaved evergreen forests [3,27,3237].
Table 1. Population studies based on genetic markers from plant and insect species inhabiting Japanese Castanopsis-type broadleaved evergreen forests [3,27,3237].
SpeciesFamilyLife FormDispersal FormNo. of PopulationsNo. of IndividualsGenome MarkersTotal Length (bp)Gene Diversity (h)Nucleotide Diversity (p)Phylogeographic Pattern (Geographic Gap)References
Plants
Elaeocarpus sylvestris var. ellipticusElaeocarpaceaeDominant treeBirds5964cpDNA4688–46890.7030.00031W-E differentiation (Kinki)Figure 1a, [3]
Prunus zippelianaRosaceaeTreeBirds7383cpDNA3838–38830.6610.00084Unique type in Kyushu and RyukyuFigure 1b, [3]
Myrsine seguiniiMyrsinaceaeTreeBirds2222cpDNA2625–26760.5060.00212W-E differentiation (Kinki to Shikoku)Figure 1c, [27]
Photinia glabraRosaceaeTreeBirds42129cpDNA4062–40870.6930.00046W-E differentiation (Chugoku)Figure 1d, [35]
Daphne kiusianaThymelaeaceaeShrubBirds1919cpDNA3378–33870.4140.00027Unique type in Kyushu[3]
Alpinia japonicaZingiberaceaePerennial herbBirds4648cpDNA2919–29450.6050.00110No clear structure[3]
Arachniodes sporadosoraDryopteridaceaeFernWind3335cpDNA349–357--No clear structure[3]
Arachniodes aristataDryopteridaceaeFernWind4141cpDNA628–662--No clear structure[3]
Castanopsis sieboldiiFagaceaeDominant treeDropping, animals, birds40937EST-SSR-0.631-W-E differentiation, unique cluster in RyukyuFigure 1e, [37]
Castanopsis cuspidataFagaceaeDominant treeDropping, animals, birds17368EST-SSR-0.741-No clear structure[37]
Insects
Curculio hilgendorfiCurculionidaeWeevilFlying but low dispersability62204mtDNA27090.9690.00624W-E differentiation (Kinki to Chugoku- Shikoku), unique clade in RyukyuFigure 1f, [32,33]
Curculio sikkimensisCurculionidaeWeevilFlying but low dispersability33115mtDNA9710.9330.00465W-E differentiation (Kinki to Chugoku- Shikoku)Figure 1g, [32,34]
Rhynchaenus dorsoplanatusCurculionidaeWeevilFlying but low dispersability55171mtDNA23430.9730.0015Unique clade in KyushuFigure 1h, [36]
Table 2. The observed genetic gap between the western and eastern parts of Japan revealed by phylogeographic studies from terrestrial plant and animal species [54,5779].
Table 2. The observed genetic gap between the western and eastern parts of Japan revealed by phylogeographic studies from terrestrial plant and animal species [54,5779].
ClassSpeciesFamilyCommon nameVegetation zoneGeographic gapReferences
PlantsPinus thunbergiiPinaceaeBlack pineWarm temperate zoneKinki to Chubu[63]
Zanthoxylum ailanthoidesRutaceaePrickly ashWarm temperate zoneChugoku-Shikoku[78]
Abies firmaPinaceaeFirWarm and cool temperate zoneKinki to Chubu[73]
Cerasus jamasakuraRosaceaeCherryWarm and cool temperate zoneKyushu-Chugoku[71]
Chamaecyparis obtusaCupressaceaeCypressWarm and cool temperate zoneKinki to Chubu[72]
Fagus crenataFagaceaeBeechCool temperate zoneKinki to Chugoku- Shikoku[57]
Fagus japonicaFagaceaeBeechCool temperate zoneKinki to Chubu[58]
Quercus mongolica var. crispulaFagaceaeOakCool temperate zoneChubu[60,66]
Quercus serrataFagaceaeOakCool temperate zoneChubu[66]
Carpinus japonicaBetulaceaeHornbeamCool temperate zoneKinki to Chugoku- Shikoku[59]
Carpinus tschonoskiiBetulaceaeHornbeamCool temperate zoneChugoku-Shikoku[59]
Carpinus laxifloraBetulaceaeHornbeamCool temperate zoneKinki-Chugoku[79]
Magnolia hypoleucaMagnoliaceae-Cool temperate zoneKinki-Chugoku[79]
Aesculus turbinataHippocastanaceaeHorse chestnutCool temperate zoneKinki[69]
CorylopsisHamamelidaceae-Cool temperate zoneKinki[75]
Viola eizanensisViolaceaeVioletCool temperate zoneChugoku-Shikoku[70]
Carex conicaCyperaceaeSedgeCool temperate zoneKinki-Chugoku[76]
Cardamine scutataBrassicaceaeHerbCool temperate and boreal zoneChubu to Tohoku[62]
InsectsXylosandrus crassiusculusScolytidaeAmbrosia beetleCool temperate zoneChubu[54]
Plateumaris sericeaChrysomelidaeLeaf beetleCool temperate zoneKinki[68]
MammalsCervus nipponCervidaeSika deerWarm and cool temperate zoneChugoku[64]
Sus scrofaSuidaeWild boarWarm and cool temperate zoneChugoku to Chubu[74]
Macaca fuscataCercopithecidaeMacaqueWarm and cool temperate zoneKinki to Chugoku- Shikoku[61]
Lepus brachyurusLeporidaeHareCool temperate zoneKinki to Chugoku- Shikoku[65]
Petaurista leucogenysSciuridaeGiant flying squirrelCool temperate zoneKinki to Chugoku- Shikoku[67]
Ursus thibetanusUrsidaeBlack bearCool temperate zoneKinki[77]

Acknowledgments

This study was partly supported by Grants-in-Aid from the Japan Society for the Promotion of Science (nos. 1701416, 21770087, and 2240030 to K. A.) and the Research Project “A new cultural and historical exploration into human-nature relationships in the Japanese archipelago” of the Research Institute for Humanity and Nature, Kyoto, Japan.

References

  1. Avise, J.C. Phylogeography: The History and Formation of Species; Harvard University Press: Cambridge, MA, USA, 2000. [Google Scholar]
  2. Hewitt, G. The genetic legacy of the Quaternary ice ages. Nature 2000, 405, 907–913. [Google Scholar]
  3. Aoki, K.; Suzuki, T.; Hsu, T.-W.; Murakami, N. Phylogeography of the component species of broad-leaved evergreen forests in Japan, based on chloroplast DNA. J. Plant Res. 2004, 117, 77–94. [Google Scholar]
  4. Arbogast, B.S.; Kenagy, G.J. Comparative phylogeography as an integrative approach to historical biogeography. J. Biogeogr. 2001, 28, 819–825. [Google Scholar]
  5. Avise, J.C. Molecular population structure and the biogeographic history of a regional fauna: A case history with lessons for conservation biology. Oikos 1992, 63, 62–76. [Google Scholar]
  6. Brochmann, C.; Gabrielsen, T.M.; Nordal, I.; Landvik, J.Y.; Elven, R. Glacial survival or tabula rasa? The history of North Atlantic biota revisited. Taxon 2003, 52, 417–450. [Google Scholar]
  7. Fujii, N.; Ueda, K.; Watano, Y.; Shimizu, T. Intraspecific sequence variation of chloroplast DNA in Pedicularis chamissonis Steven (Scrophulariaceae) and geographic structuring of the Japanese “alpine” plants. J. Plant Res. 1997, 110, 195–207. [Google Scholar]
  8. Hewitt, G.M. Genetic consequences of climatic oscillations in the Quaternary. Philos. Trans. R. Soc. Lond. Ser. B Biol. Sci. 2004, 359, 183–195. [Google Scholar]
  9. Petit, R.J.; Aguinagalde, I.; de Beaulieu, J.-L.; Bittkau, C.; Brewer, S.; Cheddadi, R.; Ennos, R.; Fineschi, S.; Grivet, D.; Lascoux, M.; et al. Glacial refugia: Hotspots but not melting pots of genetic diversity. Science 2003, 300, 1563–1565. [Google Scholar]
  10. Seo, A.; Watanabe, M.; Hotta, M.; Murakami, N. Geographical patterns of allozyme variation in Angelica japonica (Umbelliferae) and Farfugium japonicum (Compositae) on the Ryukyu Islands, Japan. Acta. Phytotax. Geobot. 2004, 55, 29–44. [Google Scholar]
  11. Soltis, D.E.; Gitzendanner, M.A.; Strenge, D.D.; Soltis, P.S. Chloroplast DNA intraspecific phylogeography of plants from the Pacific Northwest of North America. Plant Syst.Evol. 1997, 206, 353–373. [Google Scholar]
  12. Soltis, D.E.; Morris, A.B.; McLachlan, J.S.; Manos, P.S.; Soltis, P.S. Comparative phylogeography of unglaciated eastern North America. Mol.Ecol. 2006, 15, 4261–4293. [Google Scholar]
  13. Stehlik, I. Resistance or emigration? Response of alpine plants to the ice ages. Taxon 2003, 52, 499–510. [Google Scholar]
  14. Stewart, J.R.; Lister, A.M. Cryptic northern refugia and the origins of the modern biota. Trends Ecol. Evol. 2001, 16, 608–613. [Google Scholar]
  15. Taberlet, P.; Fumagalli, L.; Wust-Saucy, A.-G.; Cosson, J.-F. Comparative phylogeography and postglacial colonization routes in Europe. Mol. Ecol. 1998, 7, 453–464. [Google Scholar]
  16. Fujii, N.; Senni, K. Phylogeography of Japanese alpine plants: Biogeographic importance of alpine region of Central Honshu in Japan. Taxon 2006, 55, 43–52. [Google Scholar]
  17. Griffin, S.R.; Barrett, S.C.H. Post-glacial history of Trillium grandiflorum (Melanthiaceae) in eastern North America: Inferences from phylogeography. Am. J. Bot. 2004, 91, 465–473. [Google Scholar]
  18. Minato, M.; Ijiri, S. The Japanese Archipelago, 3rd ed.; Iwanamishoten: Tokyo, Japan, 1976. [Google Scholar]
  19. Tsukada, M. Paleoecology.II.Synthesis; Kyoritsu: Tokyo, Japan, 1974. [Google Scholar]
  20. Hotta, M. History and Geography of Plants; Sanseido: Tokyo, Japan, 1974; p. 400. [Google Scholar]
  21. Miyawaki, A.; Okuda, S. Distribution Maps of Japanese Plant Communities; Shibundo: Tokyo, Japan, 1990. [Google Scholar]
  22. Matsuoka, K.; Miyoshi, N. Chapter III-4. In The Illustrated Vegetation History of the Japanese Archipelago; Yasuda, Y., Miyoshi, N., Eds.; Asakura-shoten: Tokyo, Japan, 1998; pp. 224–236. [Google Scholar]
  23. Tsukada, M. A vegetation map in the Japanese Archipelago approximately 20,000 years B.P. Jap. J. Ecol. 1984, 34, 203–208. [Google Scholar]
  24. Chase, M.W.; Soltis, D.E.; Olmstead, R.G.; Morgan, D.; Les, D.H.; Mishler, B.D.; Duvall, M.R.; Price, R.A.; Hills, H.G.; Qiu, Y.-L.; et al. Phylogenetics of seed plants: an analysis of nucleotide sequences from the plastid gene rbcL. Ann. Mo. Bot. Gard. 1993, 80, 528–580. [Google Scholar]
  25. Frascaria, N.; Maggia, L.; Michaud, M.; Bousquet, J. The rbcL gene sequence from chestnut indicates a slow rate of evolution in the Fagaceae. Genome 1993, 36, 668–671. [Google Scholar]
  26. Wolfe, K.H.; Li, W.-H.; Sharp, P.M. Rates of nucleotide substitution vary greatly among plant mitochondrial, chloroplast, and nuclear DNAs. Biol. J. Linn.Soc. 1987, 84, 9054–9058. [Google Scholar]
  27. Aoki, K.; Hattori, T.; Murakami, N. Intraspecific sequence variation of chloroplast DNA among the component species of evergreen broad-leaved forests in Japan II. Acta. Phytotax. Geobot. 2004, 55, 125–128. [Google Scholar]
  28. Aoki, K.; Suzuki, T.; Murakami, N. Intraspecific sequence variation of chloroplast DNA among the component species of evergreen broad-leaved forests in Japan. J. Plant Res. 2003, 116, 337–344. [Google Scholar]
  29. Kamei, T. Research group for the biogeography from Würm Galacial, Fauna and flora of the Japanese Islands in the last glacial. Quaternary Res. 1981, 20, 191–205. [Google Scholar]
  30. Kuroda, T. Chapter II-9. In The Illustrated Vegetation History of the Japanese Archipelago; Yasuda, Y., Miyoshi, N., Eds.; Asakura-shoten: Tokyo, Japan, 1998; pp. 162–175. [Google Scholar]
  31. Nakanishi, S.; Ohba, T.; Takeda, Y.; Hattori, T. Illustration of Vegetation in Japan Vol. I Forest Vegetation; Hoikusha: Osaka, Japan, 1983. [Google Scholar]
  32. Aoki, K.; Kato, M.; Murakami, N. Mitochondrial DNA of phytophagous insects as a molecular tool for phylogeographic study of host plants. Acta.Phytotax.Geobot. 2005, 56, 55–69. [Google Scholar]
  33. Aoki, K.; Kato, M.; Murakami, N. Glacial bottleneck and postglacial recolonization of a seed parasitic weevil, Curculio hilgendorfi, inferred from mitochondrial DNA variation. Mol. Ecol. 2008, 17, 3276–3289. [Google Scholar]
  34. Aoki, K.; Kato, M.; Murakami, N. Phylogeographical patterns of a generalist acorn weevil: insight into the biogeographical history of broadleaved deciduous and evergreen forests. BMC Evol. Biol. 2009, 9, 103. [Google Scholar]
  35. Aoki, K.; Matsumura, T.; Hattori, T.; Murakami, N. Chloroplast DNA phylogeography of Photinia glabra (Rosaceae) in Japan. Am. J. Bot. 2006, 93, 1852–1858. [Google Scholar]
  36. Aoki, K.; Murakami, N.; Kato, M. Phylogeography of a specialist leaf-mining weevil, Rhynchaenus dorsoplanatus (Coleoptera: Curculionidae), associated with Castanopsis species. Ann. Entomol. Soc. Am. 2010, 103, 379–388. [Google Scholar]
  37. Aoki, K.; Ueno, S.; Kamijo, T.; Setoguchi, H.; Murakami, N.; Kato, M.; Tsumura, Y. Leaf structure variation, genetic diversity and demographic history of Castanopsis. 2011. unpublished work. [Google Scholar]
  38. Ueno, S.; Aoki, K.; Tsumura, Y. Generation of Expressed Sequence Tags and development of microsatellite markers for Castanopsis sieboldii var.sieboldii (Fagaceae). Ann. Forest Sci. 2009, 66, 509. [Google Scholar]
  39. Ueno, S.; Taguchi, Y.; Tomaru, N.; Tsumura, Y. Development of EST-SSR markers from an inner bark cDNA library of Fagus crenata (Fagaceae). Conserv. Genet. 2009, 10, 1477–1485. [Google Scholar]
  40. Ueno, S.; Taguchi, Y.; Tsumura, Y. Microsatellite markers derived from Quercus mongolica var.crispula (Fagaceae) inner bark expressed sequence tags. Genes Genet. Syst. 2008, 83, 179–187. [Google Scholar]
  41. Ueno, S.; Tsumura, Y. Development of ten microsatellite markers for Quercus mongolica var.crispula by database mining. Conserv. Genet. 2008, 9, 1083–1085. [Google Scholar]
  42. Yamazaki, T.; Mashiba, S. A taxonomical revision of Castanopsis cupidata (Thunb.) Schottky and the allies in Japan, Korea and Taiwan. 1. J. Jap. Bot. 1987, 62, 289–298. [Google Scholar]
  43. Yamazaki, T.; Mashiba, S. A taxonomical revision of Castanopsis cupidata (Thunb.) Schottky and the allies in Japan, Korea and Taiwan. 2. J. Jap. Bot. 1987, 62, 332–339. [Google Scholar]
  44. Kobayashi, Y.; Sugawa, T. Identification of wood of some Castanopsis species in Japan. Bull. Government Forest Exp. Station 1959, 118, 139–178. [Google Scholar]
  45. Kobayashi, S.; Hiroki, S. Patterns of occurrence of hybrids of Castanopsis cuspidata and C.sieboldii in the IBP Minamata Special Research Area, Kumamoto Prefecture, Japan. J. Phytogeogr. Taxon. 2003, 51, 63–67. [Google Scholar]
  46. Yamada, H.; Miyaura, T. Geographic occurrence of intermediate type between Castanopsis sieboldii and C.cuspidata (Fagaceae) based on the structure of leaf epidermis. J. Plant Res. 2003, 116, 477–482. [Google Scholar]
  47. Nei, M. Genetic distance between populations. Am. Nat. 1972, 106, 283–292. [Google Scholar]
  48. Iwasaki, T.; Aoki, K.; Seo, A.; Murakami, N. Intraspecific sequence variation of chloroplast DNA among the component species of deciduous broad-leaved forests in Japan. J. Plant Res. 2006, 119, 539–552. [Google Scholar]
  49. Fujii, N.; Ueda, K.; Shimizu, T. Intraspecific sequence variation of chloroplast DNA in Japanese alpine plants. J. Phytogeogr. Taxon. 1996, 44, 72–81. [Google Scholar]
  50. Du, X.; Guo, Q.; Gao, X.; Ma, K. Seed rain, soil seed bank, seed loss and regeneration of Castanopsis fargesii (Fagaceae) in a subtropical evergreen broad-leaved forest. For. Ecol. Manage. 2007, 238, 212–219. [Google Scholar]
  51. Xiao, Z.; Zhang, Z.; Wang, Y. The effects of seed abundance on seed predation and dispersal by rodents in Castanopsis fargesii (Fagaceae). Plant Ecol. 2005, 177, 249–257. [Google Scholar]
  52. Martinson, D.G.; Pisias, N.G.; Hays, J.D.; Imbrie, J.; Moore, T.C.; Shackleton, N.J., Jr. Age dating and the orbital theory of the Ice Ages: development of a high-resolution 0 to 300,000-year chronostratigraphy. Quatern. Res. 1987, 27, 1–29. [Google Scholar]
  53. Nakamura, K.; Denda, T.; Kokubugata, G.; Suwa, R.; Yang, T.Y. A.; Peng, C.I.; Yokota, M. Phylogeography of Ophiorrhiza japonica (Rubiaceae) in continental islands, the Ryukyu Archipelago, Japan. J. Biogeogr. 2010, 37, 1907–1918. [Google Scholar]
  54. Ito, M.; Kajimura, H. Phylogeography of an ambrosia beetle, Xylosandrus crassiusculus (Motschulsky) (Coleoptera: Curculionidae: Scolytinae), in Japan. Appl. Entomol. Zool. 2009, 44, 549–559. [Google Scholar]
  55. Toda, M.; Nishida, M.; Matsui, M.; Wu, G.-F.; Otaii, H. Allozyme variation among east Asian populations of the Indian rice frog, Rana limnocharis (Amphibia: Anura). Biochem. Syst. Ecol. 1997, 25, 143–159. [Google Scholar]
  56. Kizaki, K.; Oshiro, I. Paleogeography of the Ryukyu Islands.(in Japanese with English abstract). Mar. Sci. Mon. 1977, 9, 542–549. [Google Scholar]
  57. Fujii, N.; Tomaru, N.; Okuyama, K.; Koike, T.; Mikami, T.; Ueda, K. Chloroplast DNA phylogeography of Fagus crenata (Fagaceae) in Japan. Plant Syst. Evol. 2002, 232, 21–33. [Google Scholar]
  58. Hiraoka, K.; Tomaru, N. Population genetic structure of Fagus japonica revealed by nuclear microsatellite markers. Int. J. Plant Sci. 2009, 170, 748–758. [Google Scholar]
  59. Iwasaki, T.; Tono, A.; Aoki, K.; Seo, A.; Murakami, N. Phylogeography of Carpinus japonica and Carpinus tschonoskii (Betulaceae) growing in Japanese deciduous broad-leaved forests, based on chloroplast DNA variation. Acta. Phytotax. Geobot. 2010, 61, 1–20. [Google Scholar]
  60. Kanno, M.; Yokoyama, J.; Suyama, Y.; Ohyama, M.; Itoh, T.; Suzuki, M. Geographical distribution of two haplotypes of chloroplast DNA in four oak species (Quercus) in Japan. J. Plant Res. 2004, 117, 311–317. [Google Scholar]
  61. Kawamoto, Y.; Shotake, T.; Nozawa, K.; Kawamoto, S.; Tomari, K.; Kawai, S.; Shirai, K.; Morimitsu, Y.; Takagi, N.; Akaza, H.; Fujii, H.; Hagihara, K.; Aizawa, K.; Akachi, S.; Oi, T.; Hayaishi, S. Postglacial population expansion of Japanese macaques (Macaca fuscata) inferred from mitochondrial DNA phylogeography. Primates 2007, 48, 27–40. [Google Scholar]
  62. Lihová, J.; Kudoh, H.; Marhold, K. Genetic structure and phylogeography of a temperate-boreal herb, Cardamine Scutata (Brassicaceae), in northeast Asia inferred from AFLPs and cpDNA haplotypes. Am. J. Bot. 2010, 97, 1058–1070. [Google Scholar]
  63. Miyata, M.; Ubukata, M. Genetic variation of allozymes in natural stands of Japanese black pine. J. Jpn Forest Soc. 1994, 76, 445–455. [Google Scholar]
  64. Nagata, J.; Masuda, R.; Tamate, H.B.; Hamasaki, S.; Ochiai, K.; Asada, M.; Tatsuzawa, S.; Suda, K.; Tado, H.; Yoshida, M.C. Two genetically distinct lineages of the sika deer, Cervus nippon, in Japanese islands: comparison of mitochondrial D-loop region sequences. Mol. Phylogen. Evol. 1999, 13, 511–519. [Google Scholar]
  65. Nunome, M.; Torii, H.; Matsuki, R.; Kinoshita, G.; Suzuki, H. The Influence of Pleistocene refugia on the evolutionary history of the Japanese hare, Lepus brachyurus. Zool. Sci. 2010, 27, 746–754. [Google Scholar]
  66. Okaura, T.; Quang, N.D.; Ubukata, M.; Harada, K. Phylogeographic structure and late Quaternary population history of the Japanese oak Quercus mongolica var.crispula and related species revealed by chloroplast DNA variation. Genes Genet. Syst. 2007, 82, 465–477. [Google Scholar]
  67. Oshida, T.; Masuda, R.; Ikeda, K. Phylogeography of the Japanese giant flying squirrel, Petaurista leucogenys (Rodentia: Sciuridae): Implication of glacial refugia in an arboreal small mammal in the Japanese Islands. Biol. J. Linn. Soc. 2009, 98, 47–60. [Google Scholar]
  68. Sota, T.; Hayashi, M. Comparative historical biogeography of Plateumaris leaf beetles (Coleoptera: Chrysomelidae) in Japan: Interplay between fossil and molecular data. J. Biogeogr. 2007, 34, 977–993. [Google Scholar]
  69. Sugahara, K.; Kaneko, Y.; Ito, S.; Yamanaka, K.; Sakio, H.; Hoshizaki, K.; Suzuki, W.; Yamanaka, N.; Setoguchi, H. Phylogeography of Japanese horse chestnut (Aesculus turbinata) in the Japanese Archipelago based on chloroplast DNA haplotypes. J. Plant Res. 2011, 124, 75–83. [Google Scholar]
  70. Toyama, H.; Yahara, T. Comparative phylogeography of two closely related Viola species occurring in contrasting habitats in the Japanese archipelago. J. Plant Res. 2009, 122, 389–401. [Google Scholar]
  71. Tsuda, Y.; Kimura, M.; Kato, S.; Katsuki, T.; Mukai, Y.; Tsumura, Y. Genetic structure of Cerasus jamasakura, a Japanese flowering cherry, revealed by nuclear SSRs: Implications for conservation. J. Plant Res. 2009, 122, 367–375. [Google Scholar]
  72. Tsumura, Y.; Matsumoto, A.; Tani, N.; Ujino-Ihara, T.; Kado, T.; Iwata, H.; Uchida, K. Genetic diversity and the genetic structure of natural populations of Chamaecyparis obtusa: implications for management and conservation. Heredity 2007, 99, 161–172. [Google Scholar]
  73. Tsumura, Y.; Suyama, Y. Differentiation of mitochondrial DNA polymorphisms in populations of five Japanese Abies species. Evolution 1998, 52, 1031–1042. [Google Scholar]
  74. Watanobe, T.; Ishiguro, N.; Nakano, M. Phylogeography and population structure of the Japanese wild boar Sus scrofa leucomystax: mitochondrial DNA variation. Zool.Sci. 2003, 20, 1477–1489. [Google Scholar]
  75. Yamanaka, M.; Kobayashi, S.; Setoguchi, H. Distinct geographical structure across species units evidenced by chloroplast DNA haplotypes and nuclear ribosomal ITS genotypes of Corylopsis (Hamamelidaceae) in the Japanese islands. Bot. J. Linn. Soc. 2008, 157, 501–518. [Google Scholar]
  76. Yano, O.; Ikeda, H.; Hoshino, T. Phylogeography of the Japanese common sedge, Carex conica complex (Cyperaceae), based on chloroplast DNA sequence data and chromosomal variation. Am. J. Bot. 2010, 97, 1365–1376. [Google Scholar]
  77. Yasukochi, Y.; Nishida, S.; Han, S.H.; Kurosaki, T.; Yoneda, M.; Koike, H. Genetic structure of the asiatic black bear in Japan using mitochondrial DNA analysis. J. Hered. 2009, 100, 297–308. [Google Scholar]
  78. Yoshida, T.; Nagai, H.; Yahara, T.; Tachida, H. Genetic structure and putative selective sweep in the pioneer tree, Zanthoxylum ailanthoides. J. Plant Res. 2010, 123, 607–616. [Google Scholar]
  79. Iwasaki, T.; Aoki, K.; Seo, A.; Murakami, N. Comparative phylogeography of four component species of deciduous broad-leaved forests in Japan based on chloroplast DNA variation. J. Plant Res. 2011. in press. [Google Scholar]
  80. Yokoyama, Y.; Kido, Y.; Tada, R.; Minami, I.; Finkel, R.C.; Matsuzaki, H. Japan Sea oxygen isotope stratigraphy and global sea-level changes for the last 50,000 years recorded in sediment cores from the Oki Ridge. Palaeogeogr. Palaeoclimatol. Palaeoecol. 2007, 247, 5–17. [Google Scholar]
  81. Gotanda, K.; Yasuda, Y. Spatial biome changes in southwestern Japan since the Last Glacial Maximum. Quat. Int. 2008, 184, 84–93. [Google Scholar]
  82. Toju, H.; Sota, T. Phylogeography and the geographic cline in the armament of a seed-predatory weevil: effects of historical events vs.natural selection from the host plant. Mol. Ecol. 2006, 15, 4161–4173. [Google Scholar]
  83. Sota, T.; Nagata, N. Diversification in a fluctuating island setting: Rapid radiation of Ohomopterus ground beetles in the Japanese Islands. Philos. Trans. R. Soc. Lond. Ser. B Biol. Sci. 2008, 363, 3377–3390. [Google Scholar]
  84. Whiteman, N.K.; Parker, P.G. Using parasites to infer host population history: a new rationale for parasite conservation. Anim. Conserv. 2005, 8, 175–181. [Google Scholar]
  85. Nieberding, C.M.; Olivieri, I. Parasites: Proxies for host genealogy and ecology? Trends Ecol. Evol. 2007, 22, 156–165. [Google Scholar]
  86. Wirth, T.; Meyer, A.; Achtman, M. Deciphering host migrations and origins by means of their microbes. Mol. Ecol. 2005, 14, 3289–3306. [Google Scholar]
  87. Brown, W.M.; Prager, E.M.; Wang, A.; Wilson, A.C. Mitochondrial DNA sequences of primates: Tempo and mode of evolution. J. Mol. Evol. 1982, 18, 225–239. [Google Scholar]
  88. Mitton, J.B. Molecular approaches to population biology. Annu. Rev. Ecol. Syst. 1994, 25, 45–69. [Google Scholar]
  89. Palmer, J.D. Chloroplast DNA evolution and biosystematic uses of chloroplast DNA variation. Am. Nat. 1987, 130, 6–29. [Google Scholar]
  90. Herre, E.A.; Machado, C.A.; Bermingham, E.; Nason, J.D.; Windsor, D.M.; McCafferty, S.S.; VanHouten, W.; Bachmann, K. Molecular phylogenies of figs and their pollinator wasps. J. Biogeogr. 1996, 23, 521–530. [Google Scholar]
  91. Kawakita, A.; Takimura, A.; Terachi, T.; Sota, T.; Kato, M. Cospeciation analysis of an obligate pollination mutualism: Have Glochidion trees (Euphorbiaceae) and pollinating Epicephala moths (Gracillariidae) diversified in parallel? Evolution 2004, 58, 2201–2214. [Google Scholar]
  92. Weiblen, G.D. How to be a fig wasp. Annu. Rev. Entomol. 2002, 47, 299–330. [Google Scholar]
  93. DeChaine, E.G.; Martin, A.P. Using coalescent simulations to test the impact of Quaternary climate cycles on divergence in an alpine plant-insect association. Evolution 2006, 60, 1004–1013. [Google Scholar]
  94. Nieberding, C.; Morand, S.; Libois, R.; Michaux, J.R. A parasite reveals cryptic phylogeographic history of its host. Proc. R. Soc. Lond. Ser. B Biol. Sci. 2004, 271, 2559–2568. [Google Scholar]

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MDPI and ACS Style

Aoki, K.; Kato, M.; Murakami, N. Phylogeography of Phytophagous Weevils and Plant Species in Broadleaved Evergreen Forests: A Congruent Genetic Gap between Western and Eastern Parts of Japan. Insects 2011, 2, 128-150. https://doi.org/10.3390/insects2020128

AMA Style

Aoki K, Kato M, Murakami N. Phylogeography of Phytophagous Weevils and Plant Species in Broadleaved Evergreen Forests: A Congruent Genetic Gap between Western and Eastern Parts of Japan. Insects. 2011; 2(2):128-150. https://doi.org/10.3390/insects2020128

Chicago/Turabian Style

Aoki, Kyoko, Makoto Kato, and Noriaki Murakami. 2011. "Phylogeography of Phytophagous Weevils and Plant Species in Broadleaved Evergreen Forests: A Congruent Genetic Gap between Western and Eastern Parts of Japan" Insects 2, no. 2: 128-150. https://doi.org/10.3390/insects2020128

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