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468 results for “decidualization”
Deccan region, Madras, India. Genus Vandeleuria is masculine, so widely used specific name oleracea has been changed for gender agreement. Vandeleuria oleraceusis possibly a composite of species. Polytypic, but subspecific taxonomy requires reassessment. Distribution. Widespread in S Asia (India, Nepal, Bhutan, Bangladesh, and Sri Lan-ka), S China (W & S Yunnan), and mainland SE Asia N of the Isthmus of Kra. Descriptive notes. Head-body 68 mm, tail 105 mm, ear 13 mm, hindfoot 17 mm; weight 10 g. The Indomalayan Long-tailed Climbing Mouse is small, with flat nail on outer finger and outertoe; tail is slender, brown, twice as long as head-body length, and lacks distal tuft. Dorsal pelageis silky and salmon in color; venter is white, with fulvous hues. Habitat. Tall cane and tangled vines in primary and secondary forest such as bamboo forest, moist deciduous forest, temperate forests, montane wet zone, and disturbed secondary forests, and perhaps agricultural areas at elevations of 150-1500 m. Food and Feeding. Indomalayan [Long-tailed Climbing Mice eat fruits, buds, and flowers. Breeding. Litters of the Indomalayan Long-tailed Climbing Mouse have 3-6 young. Activity patterns. Indomalayan Long-tailed Climbing Mice are arboreal and nocturnal, although one individual was caught duringthe day. Movements, Home range and Social organization. Indomalayan Long-tailed Climbing Mice build nests in tall bushes or cane to rear their young. Status and Conservation. Classified as Least Concern on The IUCN Red Last (as V. olacea). The Indomalayan Long-tailed Climbing Mouse occurs in several habitats and a wide distribution that includes national parks. Further taxonomical studies are required to assess conservation status ofthis potentially diverse species complex. Bibliography. Corbet & Hill (1992), Dang Huy Huynh et al. (1994), Ellerman (1941), Marshall (1977b), Musser & Carleton (2005), Osgood (1932), Phillips (1980), Wang Yingxiang (2003). in Muridae
Deccan region, Madras, India. Genus Vandeleuria is masculine, so widely used specific name oleracea has been changed for gender agreement. Vandeleuria oleraceusis possibly a composite of species. Polytypic, but subspecific taxonomy requires reassessment. Distribution. Widespread in S Asia (India, Nepal, Bhutan, Bangladesh, and Sri Lan-ka), S China (W & S Yunnan), and mainland SE Asia N of the Isthmus of Kra. Descriptive notes. Head-body 68 mm, tail 105 mm, ear 13 mm, hindfoot 17 mm; weight 10 g. The Indomalayan Long-tailed Climbing Mouse is small, with flat nail on outer finger and outertoe; tail is slender, brown, twice as long as head-body length, and lacks distal tuft. Dorsal pelageis silky and salmon in color; venter is white, with fulvous hues. Habitat. Tall cane and tangled vines in primary and secondary forest such as bamboo forest, moist deciduous forest, temperate forests, montane wet zone, and disturbed secondary forests, and perhaps agricultural areas at elevations of 150-1500 m. Food and Feeding. Indomalayan [Long-tailed Climbing Mice eat fruits, buds, and flowers. Breeding. Litters of the Indomalayan Long-tailed Climbing Mouse have 3-6 young. Activity patterns. Indomalayan Long-tailed Climbing Mice are arboreal and nocturnal, although one individual was caught duringthe day. Movements, Home range and Social organization. Indomalayan Long-tailed Climbing Mice build nests in tall bushes or cane to rear their young. Status and Conservation. Classified as Least Concern on The IUCN Red Last (as V. olacea). The Indomalayan Long-tailed Climbing Mouse occurs in several habitats and a wide distribution that includes national parks. Further taxonomical studies are required to assess conservation status ofthis potentially diverse species complex. Bibliography. Corbet & Hill (1992), Dang Huy Huynh et al. (1994), Ellerman (1941), Marshall (1977b), Musser & Carleton (2005), Osgood (1932), Phillips (1980), Wang Yingxiang (2003).
Supplementary material 3 from: Iida T, Soga M, Koike S (2016) Effects of an increase in population of sika deer on beetle communities in deciduous forests. ZooKeys 625: 67-85. https://doi.org/10.3897/zookeys.625.9116
Table 3 : Explanation note: Estimated and observed values of beetle species richness at the island and lakeshore sites.
Supplementary material 2 from: Iida T, Soga M, Koike S (2016) Effects of an increase in population of sika deer on beetle communities in deciduous forests. ZooKeys 625: 67-85. https://doi.org/10.3897/zookeys.625.9116
Table 2 : Explanation note: Estimated and observed values of beetle abundance at the island and lakeshore sites.
Supplementary material 5 from: Iida T, Soga M, Koike S (2016) Effects of an increase in population of sika deer on beetle communities in deciduous forests. ZooKeys 625: 67-85. https://doi.org/10.3897/zookeys.625.9116
Figure 1 : Explanation note: Species accumulation curves for carabid, carrion and dung beetles at the island (blue lines) and lakeshore sites (red lines).
Supplementary material 4 from: Iida T, Soga M, Koike S (2016) Effects of an increase in population of sika deer on beetle communities in deciduous forests. ZooKeys 625: 67-85. https://doi.org/10.3897/zookeys.625.9116
Table 4 : Explanation note: Estimated and observed values of beetle diversity (Shannon-Wiener diversity index) at the island and lakeshore sites.
Supplementary Figure S1 Identification the integrity of isolated endometrium and decidual tissues using quantitative PCR.
<p>Supplementary Figure S1 Identification the integrity of isolated endometrium and decidual tissues using quantitative PCR. The typical decidualization marker genes of <em>Dtprp</em> (A) and <em>Alpl</em> (B) were determined by qRT-PCR. (C) <em>ACTA2</em> mRNA levels of the smooth muscle maker gene was examined by qRT-PCR. Results were normalized to the housekeeping gene GAPDH and presented as the mean ± SD of three separate experiments, with different letters (a, b, c) indicating statistical difference (p < 0.05; one-way ANOVA and Tukey’s test).</p>
FIGURE 1. Priogymnanthus saxicolus. A. Habitat, limestone outcrops with deciduous vegetation. B in Priogymnanthus saxicolus (Oleaceae), a new species from Minas Gerais, Brazil
FIGURE 1. Priogymnanthus saxicolus. A. Habitat, limestone outcrops with deciduous vegetation. B. Vegetative branch, not preserved. Photos by P.H.A. de Melo.
FIGURE 4 in Polypore fungus beetles (Coleoptera: Tetratomidae) in a remnant of semi-deciduous forest of the Brazilian Cerrado: checklist and the description of a new species of Eustrophopsis Champion, 1889
FIGURE 4. Illustrations of genitalia of Eustrophopsis species. (4) Median lobe of E. bilunulata Pic, 1912; (4) Ovipositor of E. laurae sp. nov. CXT, coxites; STL, stylus; VLV, vulva.
FIGURE 2. Eustrophopsis bilunulata Pic, 1912 in Polypore fungus beetles (Coleoptera: Tetratomidae) in a remnant of semi-deciduous forest of the Brazilian Cerrado: checklist and the description of a new species of Eustrophopsis Champion, 1889
FIGURE 2. Eustrophopsis bilunulata Pic, 1912, male, sampled in Malaise trap in the Parque Estadual Altamiro de Moura Pacheco, Goianápolis, Goiás, Brazil. (A) Dorsal view; (B) Ventral view.
FIGURE 1 in Polypore fungus beetles (Coleoptera: Tetratomidae) in a remnant of semi-deciduous forest of the Brazilian Cerrado: checklist and the description of a new species of Eustrophopsis Champion, 1889
FIGURE 1. Location of the Parque Estadual de Altamiro de Moura Pacheco (PEAMP), highlighting the sampling sites.
FIGURE 3 in Polypore fungus beetles (Coleoptera: Tetratomidae) in a remnant of semi-deciduous forest of the Brazilian Cerrado: checklist and the description of a new species of Eustrophopsis Champion, 1889
FIGURE 3. Eustrophopsis laurae sp. nov., female, holotype sampled in Malaise trap in the Parque Estadual Altamiro de Moura Pacheco, Goianápolis, Goiás, Brazil. (A) Dorsal view; (B) Ventral view.
FIGURE 2. Paepalanthus atratus. A. Capitulum detail. B. Leaf blade detail. C, D. Leaf apex detail. E. Scape detail. F. Spathe and scape detail. G. Spathe apex detail. H. Involucral bract, abaxial surface. I. Involucral bract, adaxial surface. J. Floral bract, abaxial surface. K. Floral bract, adaxial surface with deciduous cilia. L in Notes on an overlooked Paepalanthus (Eriocaulaceae) from central Brazil: identity, taxonomic placement, and morphological details
FIGURE 2. Paepalanthus atratus. A. Capitulum detail. B. Leaf blade detail. C, D. Leaf apex detail. E. Scape detail. F. Spathe and scape detail. G. Spathe apex detail. H. Involucral bract, abaxial surface. I. Involucral bract, adaxial surface. J. Floral bract, abaxial surface. K. Floral bract, adaxial surface with deciduous cilia. L. Staminate flower (pre-anthesis). M. Staminate flower (pre-anthesis) with sepals removed. N. Staminate flower (pre-anthesis) with sepals and petals removed. O. Pistillate flower with sepals and petals opened and lacking the stigmatic branches. P. Pistillate flower with sepals opened. Q. Pistillate flower with sepals removed and lacking the stigmatic branches. R. Gynoecium with bifid early developing stigmatic branches.
Data from: Patterns of tree mortality in a temperate deciduous forest derived from a large forest dynamics plot
Tree mortality is one of the most influential drivers of forest dynamics, and characterizing patterns of tree mortality is critical to understanding forest dynamics and ecosystem function in the present era of global change. Here, we use a unique data set of mortality in a temperate deciduous forest to characterize rates and drivers of mortality. At the 25.6-ha Center for Tropical Forest Science—Forest Global Earth Observatory forest dynamics plot at the Smithsonian Conservation Biology Institute (Virginia, USA), we conducted two full tree censuses in 2008 and 2013 and then tracked mortality over the next 2 years (2014 and 2015). Overall, the mortality rate, m, of stems ≥10 cm diameter was 1.3–2.1%/yr. Biomass mortality, M, was 1.9–3.4 Mg·ha−1·yr−1 at the stand level (0.6–1.1%/yr of biomass), less than biomass gains from growth and recruitment, resulting in net live biomass accumulation. Small stems died at the highest rate; however, contributions to M increased toward larger size classes. Most species had m < 2%/yr and M < 0.25 Mg·ha−1·yr−1 (<3%/yr of biomass), whereas two to four species had anomalously high mortality rates during each census period, accounting for 15–24% of m (n = 2, Cercis canadensis, Ulmus species) and 39–75% of M (n = 4 Quercus species). Stems that died, whether or not in association with mechanical damage, tended to grow more slowly in preceding years than surviving stems and, for certain shade-intolerant species, tended to be in neighborhoods with higher basal area. These findings show how relatively fine-scale mortality processes contribute to stand-level compositional change and carbon cycling. The mortality patterns reported here will provide a valuable basis for understanding future disturbance events within eastern deciduous forests and for comparing across forest types.
Data from: Multiple glacial refugia for cool-temperate deciduous trees in northern East Asia: the Mongolian oak as a case study
In East Asia, temperate forests are predicted to have retracted southward to c. 30° N during the last glacial maximum (LGM) based on fossil pollen data, whereas phylogeographic studies have often suggested glacial in situ survival of cool-temperate deciduous trees in their modern northern ranges. Here we report a study of the genetic diversity and structure of 29 natural Mongolian oak (Quercus mongolica) populations using 19 nuclear simple sequence repeat (nSSR) loci and four chloroplast DNA fragments. Bayesian clustering analysis with nSSRs revealed five groups, which were inferred by approximate Bayesian computation (ABC) to have diverged in multiple refugia through multiple glacial–interglacial cycles. Analysis of chloroplast DNA variation revealed four lineages that were largely but incompletely geographically disjunct. Ecological niche modelling (ENMs) indicated a southward range shift of the oak's distribution at the LGM, although high suitability scores were also evident in the Changbai Mts. (Northeast China), the Korean Peninsula, areas surrounding the Bohai Sea, and along the coast of the Russian Far East. In addition, endemic chloroplast DNA haplotypes and nuclear lineages occurred in high-latitude northern areas where the ENM predicted no suitable habitat. The combined evidence from nuclear and chloroplast DNA, and the results of the ENM clearly demonstrate that multiple northern refugia, including cryptic ones, were maintained across the current distributional range of the Mongolian oak during the LGM or earlier glacial periods. Though spatially limited, postglacial expansions from these refugia have led to a pattern of decreased genetic diversity with increasing latitude.
Data from: Habitat patch use by fishers in the deciduous forest-dominated landscape of the central Appalachian Mountains, USA
Fishers (Pekania pennanti) are often associated with the coniferous and mixed forests of the northern United States and central Canada, and their ecology has been studied extensively in portions of their distributional range. Recently, natural range expansion and reintroductions have led to recolonization by fishers of portions of the central Appalachian Mountains, USA, where deciduous forest is the dominant vegetation type. We used noninvasive hair snare surveys and microsatellite genetic analysis to detect fishers in the central Appalachian Mountains of Pennsylvania, USA. We used these detections within an occupancy modeling framework to explore habitat patch use by fishers and the forest characteristics and land use features that influenced it. We found that the likelihood of patch use by fishers was related to forests with higher proportions of low-density residential areas. Our results also suggested lower road densities might be related to higher likelihood of fisher patch use. Fishers in Pennsylvania tolerated some forms of land development. Patch use was not driven by forest type or canopy cover, at least within our deciduous forest-dominated study areas. Future research identifying the threshold values at which forest cover and land development affect patch use by fishers in the central Appalachian Mountains will better inform management decisions with respect to sites for future reintroduction of fishers.
Annual mortality and growth index for 17 tree species across entire size classes in the Ogawa Forest Reserve, an old-growth deciduous forest, central Japan
<p><span>We estimated demographic parameters across entire size classes for 17 tree species (<i>Betula</i>, <i>Carpinus</i>, <i>Fagus</i>, <i>Quercus</i>, <i>Castanea</i>, <i>Acer</i>, <i>Cerasus</i>, <i>Swida</i>, <i>Kalopanax</i>, and <i>Styrax</i>) using a dataset over 18 years obtained from the Ogawa Forest Reserve, an old-growth deciduous forest located in the southern part of the Abukuma Mountains, Ibaraki Prefecture, central Japan (36° 56', 140° 35', 610 m in elevation)<sup> 1)</sup>. Size classes were represented by 12 categories defined based on age, height, and diameter at breast height (DBH): new seedling (age < 1), aged seedling (age ≥ 1 and height < 30 cm), sapling (height 30 cm to 2 m), juvenile (height ≥ 2 m and DBH < 5 cm), D10 (DBH 5–15 cm, D10 was denoted by the midpoint of this range; later classes were similarly defined), D20, D30, D40, D50, D60, D70, and D80 (including trees with DBH ≥ 85 cm). We derived the annual mortality and growth index (i.e., the probability of a living tree transitioning to the next size class) for each species and size class using estimates of transition probabilities between size classes (i.e., stasis, progression and retrogression)<sup>2)</sup>. The stem densities of these 17 species in each size class are also presented<sup>3)</sup>.</span></p> <p><span>File list</span></p> <p><span>1) dataset - number of trees stagnating, progressing and retrogressing by size class.csv</span></p> <p><span>2) estimates - mean and 95 percent credible intervals of demographic parameters by species and size class.csv</span></p> <p><span>3) estimates - mean density of stems by species and size class.csv</span></p>
Strong non-growing season N uptake by deciduous trees in a temperate forest: A 15N isotopic experiment
<p>Nitrogen (N) is a critical element for vegetation growth and subsequent carbon (C) and nutrient cycling in terrestrial ecosystems. Plant N uptake, the only pathway for plants to directly obtain N from soils, is a bottleneck process for ecosystem C and N cycling. Ecological theories predict that deciduous trees remain dormant and do not take up N during winters as no growth occurs during this season.</p> <p>In this study, we adopted a <sup><span>15</span></sup>N isotopic experiment to trace N processes throughout the non-growing season in a temperate forest in northern China. The <sup><span>15</span></sup>N-labeled inorganic N (NH<sub><span>4</span></sub><sup><span>+</span></sup> and NO<sub><span>3</span></sub><sup><span>−</span></sup>) and <sup><span>13</span></sup>C<sup><span>15</span></sup>N-labeled organic N (glycine and tyrosine) (equivalent to 150 mg <sup><span>15</span></sup>N m<sup><span>-2</span></sup>) were applied to soils at mid-fall, and the <sup><span>15</span></sup>N recovery in various components of dominant evergreen and deciduous species was analyzed.</p> <p>We found that soil N transformation remained active in the winter and microbial N immobilization reached its peak in late winter. Surprisingly, deciduous species maintained a high N uptake that was comparable with the evergreen species throughout the non-growing season. Perennial herbs did not take up N until the next spring. All plant species acquired inorganic N and simple amino acids, while only the tree species utilized complex amino acids. Throughout the non-growing season, evergreen and deciduous trees showed higher uptake rates for NH<sub><span>4</span></sub><sup><span>+</span></sup> and glycine than NO<sub><span>3</span></sub><sup><span>−</span></sup> and tyrosine, while deciduous shrubs and herbs showed a stronger preference for NO<sub><span>3</span></sub><sup><span>−</span></sup> over other N forms.</p> <p><i>Synthesis: </i>The finding that deciduous trees have strong N uptake in the non-growing season challenges the conventional viewpoint that deciduous trees remain dormant during non-growing seasons. This mechanism might supplement the algorithm in the model representation of N-limited temperate forest ecosystems.</p>
Interactive effects of tree species mixture and climate on foliar and woody trait variation in a widely distributed deciduous tree
<p><span>Despite increasing reports of severe drought and heat impacts on forest ecosystems, c</span>ommunity-level processes, which could potentially modulate tree responses to climatic stress, are rarely accounted for. While numerous studies<span> indicate a positive effect of species diversity on a wide range of ecosystem functions and services, little is known about how species interactions influence tree responses to climatic variability. We quantified the intraspecific variation in 16 leaf and wood physiological, morphological, and anatomical traits in mature beech trees (<i>Fagus sylvatica</i> L.) at six sites located along a climatic gradient in the French Alps. At each site, we studied pure beech and mixed stands with silver fir (<i>Abies alba </i>Mill.) or downy oak (<i>Quercus pubescens </i>Willd.). We tested how functional traits differed between the two species mixtures (pure <i>vs</i>. mixed stands) within each site and along the climatic gradient. We found significant changes in many traits along the climatic gradient </span>as conditions progressively got drier and warmer<span>. Independent of the mixture, reduced leaf-level CO<sub>2</sub> assimilation, stomatal size, and thicker leaf cuticles, consistent with a more conservative resource use strategy, were found. At the drier sites, higher foliar stable carbon isotopic composition (</span><span>d</span><sup><span>13</span></sup><span>C), thicker mesophyll tissues, and lower specific leaf area (SLA) in pure stands suggests that beech had more acquisitive traits there compared to mixed stands. At the wetter sites, trees in beech-silver fir mixtures had higher chlorophyll concentration, lower </span><span>d</span><sup><span>13</span></sup><span>C, larger xylem vessels, and higher SLA, suggesting a more acquisitive resource use strategy in mixed stands than in pure stands. </span>Our work revealed that species interactions are significant modulators of functional traits, and that they can be just as important drivers of intraspecific trait variation as climatic conditions. <span>We show that downy oak mixtures lead to an adaptive drought response by common beech in dry environments. In contrast, in milder climates, interactions with silver fir seem to increase beech' resource acquisition and productivity. These findings highlight a strong context-dependency and imply that incorporating local interspecific interactions in research on climate impacts could improve our understanding and predictions of forest dynamics.</span></p>
Figure 2 in Soil oribatid mite (Acari: Oribatida) diversity and composition in semi-deciduous forest fragments in eastern Amazonia and comparison with the surrounding savanna matrix
Figure 2. Non-metric multidimensional scaling (NMDS) ordination in two dimensions of the oribatid mite community inhabiting 16 plots in savanna and 38 plots in forest fragments. Ordination was based on abundance data.
Figure 1 in Soil oribatid mite (Acari: Oribatida) diversity and composition in semi-deciduous forest fragments in eastern Amazonia and comparison with the surrounding savanna matrix
Figure 1. Map showing the Alter do Chão region, Pará, Brazil. White represents savanna vegetation; dark grey represents forest fragments and the surrounding continuous forest; light grey in the left side of the figure represents the Tapajós River. Triangles represent the 16 plots in forest fragments; black squares represent 38 plots in savanna (modified from Vasconcelos and Vilhena 2006).
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