Shohei Oumi

Complete mitochondrial DNA sequence of the endangered frog Odorrana ishikawae (family Ranidae) and unexpected diversity of mt gene arrangements in ranids

We determined the complete nucleotide sequence of the mitochondrial (mt) genome of an endangered Japanese frog, Odorrana ishikawae (family Ranidae). We also sequenced partial mt genomes of three other Odorrana and six ranid species to survey the diversity of genomic organizations and elucidate the phylogenetic problems remaining in this frog family. The O. ishikawae mt genome contained the 37 mt genes and single control region (CR) typically found in vertebrate mtDNAs, but the region of Light-strand replication origin (OL) was triplicated in this species. Four protein-encoding genes (atp6, nd2, nd3, and nd5) were found to have high sequence divergence and to be usable for population genetics studies on this endangered species. Among the surveyed ranids, only two species (Rana and Lithobates) manifested the typical neobatrachian-type mt gene arrangement. In contrast, relatively large gene rearrangements were found in Amolops, Babina, and Staurois species; and translocations of single tRNA genes (trns) were observed in Glandirana and Odorrana species. Though the inter-generic and interspecific relationships of ranid taxa remain to be elucidated based on 12S and 16S rrn sequence data, some of the derived mt gene orders were found to have synapomorphic features useful for solving problematic ranid phylogenies. The tandem duplication and random loss (TDRL) model, the traditional model for mt gene rearrangement, failed to easily explain several of the mt gene rearrangements observed here. Indeed, the recent recombination-based gene rearrangement models seemed to be more suitable for this purpose. The high frequency of gene translocations involving a specific trn block (trnH-trnS1) and several single tRNA genes suggest that there may be a retrotranslocation in ranid mt genomes.

Population structure and landscape genetics of two endangered frog species of genus Odorrana: different scenarios on two islands.

Isolation by distance and landscape connectivity are fundamental factors underlying speciation and evolution. To understand how landscapes affect gene flow and shape population structures, island species provide intrinsic study objects. We investigated the effects of landscapes on the population structure of the endangered frog species, Odorrana ishikawae and O. splendida, which each inhabit an island in southwest Japan. This was done by examining population structure, gene flow and demographic history of each species by analyzing 12 microsatellite loci and exploring causal environmental factors through ecological niche modeling (ENM) and the cost-distance approach. Our results revealed that the limited gene flow and multiple-population structure in O. splendida and the single-population structure in O. ishikawae were maintained after divergence of the species through ancient vicariance between islands. We found that genetic distance correlated with geographic distance between populations of both species. Our landscape genetic analysis revealed that the connectivity of suitable habitats influences gene flow and leads to the formation of specific population structures. In particular, different degrees of topographical complexity between islands are the major determining factor for shaping contrasting population structures of two species. In conclusion, our results illustrate the diversification mechanism of organisms through the interaction with space and environment. Our results also present an ENM approach for identifying the key factors affecting demographic history and population structures of target species, especially endangered species.

Microsatellite Marker Development by Multiplex Ion Torrent PGM Sequencing: a Case Study of the Endangered Odorrana narina Complex of Frogs

The endangered Ryukyu tip-nosed frog Odorrana narina and its related species, Odorrana amamiensis, Odorrana supranarina, and Odorrana utsunomiyaorum, belong to the family Ranidae and are endemically distributed in Okinawa (O. narina), Amami and Tokunoshima (O. amamiensis), and Ishigaki and Iriomote (O. supranarina and O. utsunomiyaorum) Islands. Because of varying distribution patterns, this species complex is an intrinsic model for speciation and adaptation. For effective conservation and molecular ecological studies, further genetic information is needed. For rapid, cost-effective development of several microsatellite markers for these and 2 other species, we used next-generation sequencing technology of Ion Torrent PGM™. Distribution patterns of repeat motifs of microsatellite loci in these modern frog species (Neobatrachia) were similarly skewed. We isolated and characterized 20 new microsatellite loci of O. narina and validated cross-amplification in the three-related species. Seventeen, 16, and 13 loci were cross-amplified in O. amamiensis, O. supranarina, and O. utsunomiyaorum, respectively, reflecting close genetic relationships between them. Mean number of alleles and expected heterozygosity of newly isolated loci varied depending on the size of each inhabited island. Our findings suggested the suitability of Ion Torrent PGM™ for microsatellite marker development. The new markers developed for the O. narina complex will be applicable in conservation genetics and molecular ecological studies.

Artificial Production and Natural Breeding of the Endangered Frog Species Odorrana ishikawae, with Special Reference to Fauna Conservation in the Laboratory

Odorrana ishikawae is listed as a class IB endangered species in the IUCN Red List and is protected by law in both Okinawa and Kagoshima Prefectures, Japan. Here, in an effort to help effectively preserve the genetic diversity of this endangered species in the laboratory, we tested a farming technique involving the artificial breeding of frogs, and also promoted natural breeding in the laboratory. Field-caught male/female pairs of the Amami and Okinawa Island populations were artificially bred using an artificial insemination method in the 2004, 2006, and 2008 breeding seasons (March to April). Although fewer than 50% of the inseminated eggs achieved metamorphosis, approximately 500, 300, and 250 offspring from the three respective trials are currently being raised in the laboratory. During the 2009 and 2010 breeding seasons, second-generation offspring were produced by the natural mating activities of the first offspring derived from the two artificial matings in 2004. The findings and the methods presented here appear to be applicable to the temporary protection of genetic diversity of local populations in which the number of individuals has decreased or the environmental conditions have worsened to levels that frogs are unable to survive by themselves.

Isolation and characterization of ten microsatellite loci of endangered Anderson’s crocodile newt, Echinotriton andersoni

Due to an originally small distribution range and recent habitat loss, Anderson’s crocodile newt (Echinotriton andersoni) has been steadily declining in number. For effective conservation of this species, a greater amount of genetic information is needed. Here, we isolated ten microsatellite loci of E. andersoni using three different methods, and polymorphism of these 10 loci were evaluated for 27 individuals collected from three islands. The total number of alleles per locus ranged from 3 to 22, and the expected heterozygosity ranged from 0 to 0.876. Taken together, our findings suggest that these novel loci will be applicable for conservation genetic studies across varying scales.

An Attempt at Captive Breeding of the Endangered Newt Echinotriton andersoni, from the Central Ryukyus in Japan

Simple Summary We naturally bred the endangered Anderson’s crocodile newt (Echinotriton andersoni) and tested a laboratory farming technique using near-biotopic breeding cages with several male and female pairs collected from Okinawa, Amami, and Tokunoshima Islands. This is the first published report of successfully propagating an endangered species by using breeding cages in a laboratory setting for captive breeding. Our findings on the natural breeding and raising of larvae and adults are useful in breeding this endangered species, and can be applied to the preservation of other similarly wild and endangered species. Abstract Anderson’s crocodile newt (Echinotriton andersoni) is distributed in the Central Ryukyu Islands of southern Japan, but environmental degradation and illegal collection over the last several decades have devastated the local populations. It has therefore been listed as a class B1 endangered species in the IUCN Red List, indicating that it is at high risk of extinction in the wild. The species is also protected by law in both Okinawa and Kagoshima prefectures. An artificial insemination technique using hormonal injections could not be applied to the breeding of this species in the laboratory. In this study we naturally bred the species, and tested a laboratory farming technique using several male and female E. andersoni pairs collected from Okinawa, Amami, and Tokunoshima Islands and subsequently maintained in near-biotopic breeding cages. Among 378 eggs derived from 17 females, 319 (84.4%) became normal tailbud embryos, 274 (72.5%) hatched normally, 213 (56.3%) metamorphosed normally, and 141 (37.3%) became normal two-month-old newts; in addition, 77 one- to three-year-old Tokunoshima newts and 32 Amami larvae are currently still growing normally. Over the last five breeding seasons, eggs were laid in-cage on slopes near the waterfront. Larvae were raised in nets maintained in a temperature-controlled water bath at 20 °C and fed live Tubifex. Metamorphosed newts were transferred to plastic containers containing wet sponges kept in a temperature-controlled incubator at 22.5 °C and fed a cricket diet to promote healthy growth. This is the first published report of successfully propagating an endangered species by using breeding cages in a laboratory setting for captive breeding. Our findings on the natural breeding and raising of larvae and adults are useful in breeding this endangered species and can be applied to the preservation of other similarly wild and endangered species such as E. chinhaiensis.