Negative effects of deep roadside ditches on Pelophylax porosa brevipoda dispersal and migration in comparison with Hyla japonica in a rice paddy area in Japan

In Japan, rice paddies have acted as a substitute habitat for pond-breeding frogs. However, since the 1950s, agricultural modernization has altered the rice paddy environment, and pond-breeding frog populations have been decreasing. This agricultural modernization has led to rice paddy fragmentation via roadways and the construction of deep channels. To assess the influences of habitat fragmentation, we compared the distribution of two pond-breeding frogs, a common species, Hyla japonica, and an endangered species, Pelophylax porosa brevipoda, around a deep roadside ditch. In Shiga prefecture, we selected two rice paddies along a roadway and recorded the number of frogs and their snout-vent length (SVL) at the levee of a rice paddy, ditch, bank, and adjacent roadway. In total, we identified 1,293 P. p. brevipoda and 181 H. japonica. Most P. p. brevipoda were either at the levee or ditch, and the number of this species found in the ditch was much higher than in any other location in July and October. The SVLs of P. p. brevipoda found in the ditch in June were smaller than those in October. Most H. japonica were at the levee or bank, and there were no apparent temporal or spatial patterns of distribution. Our results suggest that the ditch acts as a barrier to juveniles in early summer and to all frogs during autumn for P. p. brevipoda but not for H. japonica. For long-term conservation, it is important to study the movement patterns related to life history and rice paddy management.     

Obligate crayfish burrow use and core habitat requirements of crawfish frogs

Crawfish frogs (Lithobates areolatus) have experienced declines across large portions of their former range. These declines are out of proportion to syntopic wetland-breeding amphibian species, suggesting losses are resulting from unfavorable aspects of non-breeding upland habitat. Crawfish frogs get their common name from their affinity for crayfish burrows, although the strength of this relationship has never been formally assessed. We used radiotelemetry to address 4 questions related to upland burrow dwelling in crawfish frogs: 1) what burrow types are used and how do they function to affect crawfish frog survivorship; 2) what are the physical characteristics and habitat associations of crawfish frog burrows; 3) what are the home range sizes of crawfish frogs when burrow dwelling; and 4) where are crawfish frog burrows situated with respect to breeding wetlands? We tracked crawfish frogs to 34 burrows, discovered another 7 occupied burrows, and therefore report on 41 burrows. Crawfish frogs exclusively occupied crayfish burrows as primary burrows, which they inhabited for an average of 10.5 months of the year. With one exception, crawfish frogs also used crayfish burrows as secondary burrows—temporary retreats occupied while exhibiting breeding migrations or ranging forays. Burrows were exclusively located in grassland habitats, although crawfish frogs migrated through narrow woodlands and across gravel roads to reach distant grassland primary burrow sites. Home range estimates while inhabiting burrows were 0.05 m² (the area of the burrow entrance plus the associated feeding platform) or 0.01 m³ (the estimated volume of their burrow). Crawfish frog burrows were located at distances up to 1,020 m from their breeding wetlands. To protect crawfish frog populations, we recommend a buffer (core habitat plus terrestrial buffer) of at least 1.2 km around each breeding wetland. Within this buffer, at least 3 critical habitat elements must be present: 1) extensive grasslands maintained by prescribed burning and/or logging, 2) an adequate number of upland crayfish burrows, and 3) no soil disturbance of the sort that would destroy crayfish burrow integrity. © 2012 The Wildlife Society.     

Insular shifts in body size of rice frogs in the Zhoushan Archipelago, China

1. Differences in body size between mainland and island populations have been reported for reptiles, birds and mammals. Despite widespread recognition of insular shifts in body size in these taxa, there have been no reports of such body size shifts in amphibians. 2. We provide the first evidence of an insular shift in body size for an amphibian species, the rice frog Rana limnocharis. We found significant increases in body size of rice frogs on most sampled islands in the Zhoushan archipelago when compared with neighbouring mainland China. 3. Large body size in rice frogs on islands was significantly related to increased population density, in both breeding and non-breeding seasons. Increases in rice frog density were significantly related to higher resource availability on islands. Increased resource availability on islands has led to higher carrying capacities, which has subsequently facilitated higher densities and individual growth rates, resulting in larger body size in rice frogs. We also suggest that large body size has evolved on islands, as larger individuals are competitively superior under conditions of harsh intraspecific competition at high densities. 4. Increases in body size in rice frogs were not related to several factors that have been implicated previously in insular shifts in body size in other taxa. We found no significant relationships between body size of rice frogs and prey size, number of larger or smaller frog species, island area or distance of islands from the mainland. 5. Our findings contribute to the formation of a broad, repeatable ecological generality for insular shifts in body size across a range of terrestrial vertebrate taxa, and provide support for recent theoretical work concerning the importance of resource availability for insular shifts in body size.     

Bat activity and species richness in different land‐use types in and around Chome Nature Forest Reserve,Tanzania

Bats have important ecological roles in ecosystems, but many species are threatened because of anthropogenic impacts. Tanzania has limited information on how bats respond to habitat modification. This makes it difficult to anticipate which bat species are at risk. Bat activity and species richness were assessed in five land‐use types: forest and banana–coffee (upland habitats), rice paddy, riverine and sisal estate (lowland habitats). Mist nets, harp traps and bat detectors were used to sample bats. Species richness differed between habitats. Bat activity levels were higher in lowland habitats than upland habitats. Riverine and rice paddy habitats were shown to have an important role as foraging sites for many insectivorous bats as bat species richness and activity were generally higher than other habitats. Fruit‐eating bats preferred riverine and banana–coffee habitats. We recommend using organic manure as alternatives to chemical fertilisers, and pesticide use should be avoided in rice paddies. Riparian vegetation along rivers and water bodies should be maintained as important faunal nesting, roosting and/or foraging grounds. The requirement that farming practices be at least 60 m from the river should be strictly enforced. These recommendations will help in the conservation of bats and their habitats in modified agricultural landscapes.     

Reptiles and frogs use most land cover types as habitat in a fine‐grained agricultural landscape

Agricultural landscapes comprise much of the earth's terrestrial surface. However, knowledge about how animals use and move through these landscapes is limited, especially for small and cryptic taxa, such as reptiles and amphibians. We aimed to understand the influence of land use on reptile and frog movement in a fine‐grained grazing landscape. We surveyed reptiles and frogs using pitfall and funnel traps in transects located in five land use types: 1) woodland remnants, 2) grazed pastures, 3) coarse woody debris added to grazed pastures, 4) fences in grazed pastures and 5) linear plantings within grazed pastures. We found that the different land cover types influenced the types and distances moved by different species and groups of species. Reptiles moved both within, and out of, grazed paddocks more than they did in woodland remnants. In contrast, frogs exhibited varying movement behaviours. The smooth toadlet (Uperoleia laevigata) moved more often and longer distances within remnants than within paddocks. The spotted marsh frog (Limnodynastes tasmaniensis) moved out of grazed pastures more than out of pastures with coarse woody debris added or fences and were never recaptured in plantings. We found that most recaptured reptiles and frogs (76.3%) did not move between trapping arrays, which added to evidence that they perceived most of the land cover types as habitat. We suggest that even simple fences may provide conduits for movement in the agricultural landscape for frogs. Otherwise, most reptile and frog species used all land cover types as habitat, though of varying quality. Reptiles appeared to perceive the woodland remnants as the highest quality habitat. This landscape is fine‐grained which may facilitate movement and persistence due to high heterogeneity in vegetation cover over short distances. Therefore, intensification and increasing the size of human land use may have negative impacts on these taxa.     

Forest Fragment and Breeding Habitat Characteristics Explain Frog Diversity and Abundance in Singapore

Habitat loss and fragmentation can have severe negative and irreversible effects on biodiversity. We investigated the effects of forest fragmentation on frog diversity in Singapore because of its high rates of deforestation and the demonstration that frogs are some of the most sensitive species to habitat degradation. We surveyed frog species in 12 forest fragments varying from 11 to 935 ha. We compared differences in species richness, abundance, and Shannon's index in relation to forest fragment size, connectivity (distance between fragments), and breeding habitat heterogeneity. A total of 20 species from 12 genera and five families were encountered in 12 fragments. Larger fragments and those closer to larger fragments had higher species richness. Abundance, however, was not correlated with forest area or connectivity, but we found fewer individual frogs in the larger fragments. We also found that breeding habitat heterogeneity best explained frog species diversity and abundance in forest fragments. Fragments with a high diversity of breeding habitats had more species. We found no evidence to suggest that abundance and diversity are strongly correlated, particularly in disturbed areas, but that breeding habitat heterogeneity is an under-appreciated factor that should be considered when prioritizing areas for anuran conservation. Enriching breeding habitat heterogeneity, creating corridors between fragments, and reforesting degraded areas are some of the most beneficial strategies for preserving urban frog biodiversity.     

Winter bird communities in the northern Negev: species dispersal patterns, habitat use and implications for habitat conservation

Bird habitat conservation may require different management strategies for different seasonal bird assemblages. We studied habitat use by winter birds in forest and scrubland habitat patches in the northern Negev, Israel. Our goal was to assess whether differences in responses to landscape and habitat structure between breeding and non-breeding seasons require changes in future conservation plans that have been suggested for the Negev breeding bird community. We evaluated habitat and area effects on bird abundance and distribution and tested whether species habitat use during winter involves niche shifts. Compared with breeding birds, a larger proportion of winter bird species occupied both scrubland and forest. As in summer, forest bird species responded to habitat structure, whereas scrubland species were associated with both habitat structure and area. Resident birds disperse into habitats in which they were not present during summer. Consequently, for several species, the correlation between bird densities and environmental factors showed a better fit at the landscape rather than at the habitat scale. In addition, rather than niche shift, birds actually extended their niche breadth. Nest site selection may constrain bird distribution into a realized niche, smaller than their fundamental niche. Despite the scale differences in habitat use, the similar species diversity patterns between seasons suggest that both winter and summer birds would benefit from conservation of scrub patches larger than 50 ha, and enrichment of foliage layers within the planted forests.     

How the environment shapes animal signals: a test of the acoustic adaptation hypothesis in frogs

Long‐distance acoustic signals are widely used in animal communication systems and, in many cases, are essential for reproduction. The acoustic adaptation hypothesis (AAH) implies that acoustic signals should be selected for further transmission and better content integrity under the acoustic constraints of the habitat in which they are produced. In this study, we test predictions derived from the AAH in frogs. Specifically, we focus on the difference between torrent frogs and frogs calling in less noisy habitats. Torrents produce sounds that can mask frog vocalizations and constitute a major acoustic constraint on call evolution. We combine data collected in the field, material from scientific collections and the literature for a total of 79 primarily Asian species, of the families Ranidae, Rhacophoridae, Dicroglossidae and Microhylidae. Using phylogenetic comparative methods and including morphological and environmental potential confounding factors, we investigate putatively adaptive call features in torrent frogs. We use broad habitat categories as well as fine‐scale habitat measurements and test their correlation with six call characteristics. We find mixed support for the AAH. Spectral features of torrent frog calls are different from those of frogs calling in other habitats and are related to ambient noise levels, as predicted by the AAH. However, temporal call features do not seem to be shaped by the frogs’ calling habitats. Our results underline both the complexity of call evolution and the need to consider multiple factors when investigating this issue.     

An historical interpretation of habitat use by frogs in a Central Amazonian Forest

Interpretations of habitat use in tropical frog assemblages have centred on resource partitioning and stressed the influence of interspecific interaction and climatic fluctuation on numbers of species using various habitats. We used audio strip transects and visual methods to determine the species composition, reproductive modes, and habitat occupancy patterns of the entire assemblage of frog species in 1900 hectares of primary forest north of Manaus in the central Amazon. We then compared taxon, reproductive mode, and habitat of species at six analogous lowland forest sites of similar species richness (five in the Amazon and one in Southeast Asia) to determine similarity of habitat use among sites and whether habitat is strongly associated with species» systematic positions. In all lowland Amazonian faunas, most species with aquatic development use pools, many species undergo some degree of terrestrial development, and few species are riparian or develop in streams. In contrast, about half the species in Southeast Asian assemblages are riparian and develop in streams, and few species develop terrestrially. Because reproductive mode and habitat associate strongly with taxon, patterns of habitat use observed at this regional scale are better explained by historical biogeography and differential rates of speciation than by proximal selection generated by contemporary environmental conditions. This study presents an inventory of frog species in a central Amazonian terre-firme forest and measurements of habitat availability and use by an entire assemblage of frogs throughout a large area (other portions of this study were published by Gascon, 1990, 1991; Zimmerman & Rodrigues, 1990; Zimmerman, 1991). We asked whether this local pattern of habitat occupancy differed from the regional Amazonian pattern and whether local species composition could be predicted from (sub)habitat composition. Viewing the assemblage at the local level did reveal species-(sub)habitat relationships masked at the broader regional level. About half the pool-breeders at the Manaus forest study sites would not use pools that could be flooded by a permanent stream; several species distinguished between permanent and temporary ponds; and some species occupied all available breeding habitat, whereas others occurred patchily. This pattern was maintained over four breeding seasons, and species composition could be predicted from (sub)habitat composition. Phylogeny was not a predictor of subhabitat occupancy. Perhaps species are phylogenetically constrained to develop in pool, stream, riparian, or terrestrial habitats, but contemporary selection governs their narrow distribution within these major habitat types. Finally, we asked whether anuran species richness in the central Amazon differs from that of the upper or lower Amazon. One genus, Eleutherodactylus , accounts for elevated species richness at upper Amazonian sites. Dry seasons in the central and lower Amazon are unlikely to restrict the spread of eleutherodactylines, which reproduce terrestrially. There are as many non-eleutherodactylines with terrestrial development at seasonal sites as there are at continually wet sites. Colonization history and the topography of central and lower Amazonia are more likely to limit eleutherodactyline richness.     

Effects of environmental factors on the ecology and survival of a widespread,endemic Cerrado frog

Understanding the mechanisms that affect habitat use by vertebrates is critical for understanding how species are distributed across landscapes and how they cope with habitat change. The Brazilian Savanna (the Cerrado) has vegetation ranging from grassland to woodland savannas and harbors a rich and diverse amphibian fauna impacted by accelerated habitat loss. Here, we test the influence of vegetation type (from grassy scrubland to woodland) and distance from breeding sites (ephemeral water bodies) on body size, abundance, and survival of the frog Physalaemus nattereri in a natural metapopulation system of south-central Brazil. We also test whether body size is a significant predictor of population abundance. We found that the abundance of P. nattereri varies according to the mean snout–vent length of each metapopulation (sampling unit), as well as a higher estimated mortality rate in woodlands compared with typical Cerrado. Furthermore, we found no difference in estimated mortality among sampling units located far or close to ephemeral water bodies. Thus, our results highlight variable responses of P. nattereri metapopulations to environmental factors, despite the observed high heterogeneity among sampled habitats and the importance of ephemeral water bodies for reproduction. These findings highlight that land cover and availability of breeding sites might not always interact to explain population persistence of Cerrado frogs.     

Impact of post-European stream change on frog habitat: southeastern Australia

Stream geomorphology and fluvial processes in Australia have generallybeen modified substantially since European settlement. In the case of theSouthern Tablelands of New South Wales, in southeastern Australia, detailednotes of early explorers and settlers and early survey maps have providedinsight into the nature of these changes. Early explorers described most streamsin this area as 'chains-of-ponds'. These are ponds connected byshort lengths of channel or divided by grassy intervals. Many of these systemswere converted to incised channels after Europeans arrived. An examination ofthe life history characteristics of frogs and their physiological limitationsprovides insight into how these changes are likely to have affected froghabitat. Chains-of-ponds provided permanent breeding ponds for frog species withextended larval stages. The environment surrounding these ponds floodedregularly, providing breeding habitat for species that can exploit ephemeralwaterbodies. Flood waters and saturated soil also created moist, well-vegetatedenvironments for adult frogs during the non-breeding season. Human impacts andlandscape modification led to channel incision of chain-of-pond systems andresulted in many physical changes in pond characteristics, includingavailability, permanency, structural complexity and flow dynamics. Theimplications of these changes are discussed in this paper. Hypotheses aredeveloped on frog species susceptibility to landscape change associated withchannel incision of chain-of-pond systems.     

Circannual variation in habitat use of the White-winged Snowfinch Montifringilla nivalis nivalis

High mountain areas are subject to strong seasonal fluctuations, and species inhabiting these particular environments show a high degree of habitat specialization to cope with extreme abiotic conditions. Estimates of habitat use are influenced by the spatial and seasonal scales at which they are evaluated, so studies at multiple scales are important in order to explore adaptive responses to seasonal environments. In the present study, we assessed habitat use of the White-winged Snowfinch Montifringilla nivalis subsp. nivalis (henceforth Snowfinch) during breeding and non-breeding seasons at three different spatial scales (diameters of 100, 250 and 500 m). Although Snowfinches clearly used high-elevation habitats in both seasons, there was evidence that they are less specific during the non-breeding period: the variance explained by habitat and topographical factors was lower in winter than in the breeding season. Moreover, our results suggest that the use of habitat is scale-dependent. This pattern was especially relevant in the breeding season, perhaps because habitat use might be more related to nest-site selection and specific foraging sites to provide food for nestlings. Snowfinches use high mountain habitats throughout the year, probably as a consequence of physiological and morphological specializations typical of high-elevation species, but in winter they show a certain flexibility in habitat use. Snowfinches might thus adopt a flexible specialist strategy. This could represent a trade-off to overcome possible effects on survival, condition and fitness, which can be particularly strong in harsh, unpredictable environments.     

崇明东滩冬季不同管理模式下水稻田水鸟群落特征及其生境分析

崇明东滩是亚太地区候鸟迁徙路线的重要中转站,也是上海地区促淤圈围的重点区域。水稻(Oryza sativa)田作为当地分布广泛且重点改造的人工湿地,研究其是否具有水鸟招引效果具有重要意义。本研究于2013和2014年冬季采用样方法对崇明东滩两种不同管理模式的水稻田,即2013年开始改造的传统模式水稻田和改造多年的机械化模式水稻田,进行了水鸟群落及生境因子调查,以探究不同管理模式下水稻田内生境差异,水鸟对不同生境的利用程度及其不同生境中的关键因子对水鸟分布的影响。调查期间共记录到水鸟5目7科18种1 795只次,其中传统模式水稻田记录到水鸟5目6科17种1 756只次,优势种为绿翅鸭(Anas crecca)、斑嘴鸭(A.poecilorhyncha)、鹤鹬(Tringa erythropus);机械化模式水稻田录到水鸟4目5科6种39只次,优势种为小??(Tachybaptus ruficollis)和凤头麦鸡(Vanellus vanellus)。T检验结果显示,传统模式水稻田对水鸟的招引效果(即多度和物种丰富度)显著优于机械化模式水稻田,2014年改造后传统模式水稻田的水鸟招引效果显著优于2013改造初期。多元回归分析显示,明水面面积比例是影响水稻田水鸟种类、数量分布的最重要因子。结果表明,明水面面积和适合的水位高度是影响冬季水稻田水鸟招引效果的主要因素,为提高冬季水稻田水鸟保育效果,应注重营造、维护冬季水稻田中水文条件。     

红瘰疣螈的繁殖生态

红瘰疣螈(Tylototriton shanjing)为国家Ⅱ级重点保护野生动物,对其繁殖生态尚无系统的研究。2007～2010年在云南省新平县哀牢山对红瘰疣螈形态、繁殖栖息地、求偶和交配行为、产卵及孵化等繁殖特征进行了研究。结果表明,红瘰疣螈雌雄两性在广泛的形态学度量特征上存在着差异;繁殖栖息地主要为稻田和潮湿的沟渠;参与繁殖的雌雄成体性比随繁殖时间的推移而不断变化,繁殖前期和后期雄性比例高,中期雌性比例高。求偶和交配主要在陆地潮湿的水沟中完成,也可在静水中进行。成体产卵活动从5月初持续至6月下旬,呈现出波浪式的产卵进程,个体完成产卵平均时间为(22.2±2.7)h。繁殖前期雌螈产卵于稻田,中后期产于多杂草的田埂草丛和泥壁,平均产卵数(126±18)枚(n=17)。平均孵化期(17.3±0.1)d(n=225),孵化率59.8%(n=79),孵化时幼体平均体长12.7mm(n=6)。     

Taxonomic composition and ploidy level among European water frogs (Anura: Ranidae: Pelophylax) in eastern Hungary

The western Palaearctic water frogs in the genus Pelophylax comprise several distinct species and three hybridogenetic hybrid forms. In this study, we focus on the Pelophylax esculentus complex, which consists of two sexual species, Pelophylax ridibundus and Pelophylax lessonae, and their hybridogenetic hybrid, Pelophylax esculentus. Specifically, we investigated taxonomic composition and ploidy level of water frogs sampled in three different types of wetland habitats in the Hortobágy National Park (HNP), eastern Hungary. Using variation in serum albumin intron 1 (SAI‐1) and 15 microsatellite loci, we detected the presence of all members of the P. esculentus complex in the studied localities. In one locality, all three taxa occurred syntopically, while in others water frog populations consisted of P. ridibundus and P. esculentus exclusively. The genomic composition of the 63 examined hybrid specimens analysed with microsatellites showed the occurrence of diploid genotypes only. We used a population genetic approach (allelic richness, gene diversity, multilocus genotypes and multilocus disequilibrium) to infer the breeding system of water frogs at HNP. Our data indicate that at least in two populations, hybrids form gametes with clonally transmitted P. ridibundus genome and produce a new hybrid generation by mating with P. lessonae.     

Mechanistic insights into landscape genetic structure of two tropical amphibians using field‐derived resistance surfaces

Conversion of forests to agriculture often fragments distributions of forest species and can disrupt gene flow. We examined effects of prevalent land uses on genetic connectivity of two amphibian species in northeastern Costa Rica. We incorporated data from field surveys and experiments to develop resistance surfaces that represent local mechanisms hypothesized to modify dispersal success of amphibians, such as habitat‐specific predation and desiccation risk. Because time lags can exist between forest conversion and genetic responses, we evaluated landscape effects using land‐cover data from different time periods. Populations of both species were structured at similar spatial scales but exhibited differing responses to landscape features. Litter frog population differentiation was significantly related to landscape resistances estimated from abundance and experiment data. Model support was highest for experiment‐derived surfaces that represented responses to microclimate variation. Litter frog genetic variation was best explained by contemporary landscape configuration, indicating rapid population response to land‐use change. Poison frog genetic structure was strongly associated with geographic isolation, which explained up to 45% of genetic variation, and long‐standing barriers, such as rivers and mountains. However, there was also partial support for abundance‐ and microclimate response‐derived resistances. Differences in species responses to landscape features may be explained by overriding effects of population size on patterns of differentiation for poison frogs, but not litter frogs. In addition, pastures are likely semi‐permeable to poison frog gene flow because the species is known to use pastures when remnant vegetation is present, but litter frogs do not. Ongoing reforestation efforts will probably increase connectivity in the region by increasing tree cover and reducing area of pastures.     

Potential impact of genome exclusion by alien species in the hybridogenetic water frogs (<Emphasis Type="Italic">Pelophylax esculentus</Emphasis> complex)

Globalization and increasing human impact on natural aquatic systems have facilitated the movement of species and the establishment of nonindigenous species enhancing hybridisation opportunities between naturally allopatric species. In this review, we focus on a special case of natural hybrid speciation and the consequences of recent anthropogenic hybridisation in the water frog complex (Pelophylax esculentus complex), which consists of two parental species, Pelophylax lessonae and Pelophylax ridibundus and a hybrid taxon. The hybrid water frogs reproduce hybridogenetically and eliminate the genome of the syntopic water frog species. Although the actual cause triggering chromosome exclusion remains elusive, it has been proposed that chromosome elimination takes place prior to meiosis and may involve enzymatic degradation of the discarded genome. Translocations of water frogs in Western Europe have become frequent the last decade leading to rapid expansion of the range of the marsh frog P. ridibundus. Subsequent hybridisation of the exotic P. ridibundus may dramatically affect the viability and maintenance of hybrid water frog populations throughout Europe. Interestingly, the impact of this introduced species may differ depending on their geographic origin, which defines the ability to induce genome elimination. This may result in fertile or sterile hybrids, making global conservation guidelines challenging. We predict a severe genetic and ecological impact of nonindigenous P. ridibundus prompting for strict conservation measures to reduce species translocations and for studies on the geographic origin of exotic frog species.     

Niche modeling for management-ready information in little-studied,threatened frog species assemblages

We use species distribution modeling to create easily testable hypotheses about the current and future distributions of Jamaican frogs, a little studied but highly endangered group. Our models simultaneously represent the best possible current estimate of the frogs’ ranges and provide clear guidelines for future survey work and habitat preservation efforts. We identify areas that contain the highest frog biodiversity, the highest per-unit area frog conservation benefit, and areas that are putative climatic refuges from outbreaks of the frog disease chytridiomycosis. In addition, we use the distribution models to create a set of easily falsifiable predictions about frog presence or absence. Testing these predictions using presence/absence surveys will provide management-ready information about model quality, population trajectories, changes in realized climate tolerance, and disease presence. We present a method of generating targeted conservation recommendations that will be applicable to many little-studied, cryptic taxa worldwide.     

Evidence that creation of a Pinus radiata plantation in south-eastern Australia has reduced habitat for frogs

Loss and fragmentation of habitat resulting from the clearing of forests for agriculture and urban development threaten the persistence of thousands of species worldwide. The clearing of native forest to plant a monoculture of exotic trees may also reduce and fragment the habitat available for indigenous plants and animals. Metacommunity theory suggests that the species richness of a community in a patch of habitat will increase with patch size but decrease with patch isolation. We investigated whether replacement of native Eucalyptus forest with a plantation of Pinus radiata has reduced and fragmented habitat for frogs, leading to a lower species richness of frog communities in the pine plantation and in small and/or isolated remnant patches of native forest. We surveyed frogs at 60 sites at streams and wetlands in the pine plantation, remnant patches of native forest surrounded by pines, and adjacent areas of contiguous native forest near Tumut in New South Wales, Australia. Only two of eight species of frogs were recorded in the pine plantation, and regression modelling indicated that streams and wetlands in the pines supported fewer frog species than those in remnant patches or the intact native forest. In addition, species richness tended to be higher at wide, shallow swamps and marshes near the headwaters of streams, with herbs, grasses, shrubs, reeds, sedges and rushes in the emergent and fringing vegetation. There was little evidence to suggest that larger eucalypt remnants supported more species of frogs, or that remnants isolated by greater expanses of pines supported fewer species, but we had low power to detect these effects with our data set. Our results support the preservation of all remnants of native forest along drainage lines and around swamps, soaks and bogs, regardless of size. Where new pine plantations are established, for example, on cleared agricultural land, care should be taken to maintain the structural and vegetative characteristics of water bodies to ensure that they continue to provide suitable breeding habitat for frogs.     

Balance between site fidelity and habitat preferences in colony site selection by herons and egrets

Habitat selection in avian species is a hierarchical process driven by different factors acting at multiple scales. Habitat preferences and site fidelity are two main factors affecting how colonial birds choose their breeding locations. Although these two factors affect how colonial species choose their habitats, previous studies have only focused on one factor at a time to explain the distribution of species at regional scales. Here we used 28 yr of colony location data of herons and egrets around Ibaraki prefecture in Japan in order to analyze the relative importance of habitat preferences and colony site fidelity for selecting breeding locations. We used Landsat satellite images together with a ground survey‐based map to create land‐use maps for past years and determine the habitats surrounding the herons and egrets colonies. Combining the estimated colony site fidelity with the habitat data, we used a random forest algorithm to create habitat selection models, which allowed us to analyze the changes in the importance of those factors over the years. We found high levels of colony site fidelity for each year of study, with its relative importance as a predictor for explaining colony distribution increasing drastically in the most recent five years. The increase in collective site fidelity could have been caused by recent changes in the population size of grey herons Ardea cinerea, a key species for colony establishment. We observed a balance between habitat preferences and colony site fidelity: habitat preferences were a more powerful predictor of colony distribution until 2008, when colony site fidelity levels were lower. Considering changes in the relative importance of these factors can lead to a better understanding of the habitat selection process and help to analyze bird species’ responses to environmental changes.