ライフサイエンスコーパス: conifer

1 an approximation-based methods (e.g. XHMM or CoNIFER).

2 during the end stages of mortality in these conifers.

3 allitris, the world's most drought-resistant conifers.

4 ng role of aridity in the diversification of conifers.

5 ial variation in the density of regenerating conifers.

6 ly stable N2 -fixing strategy for long-lived conifers.

7 lowest of all in streams draining non-native conifers.

8 ic and respiratory fluxes from high-latitude conifers.

9 is method can be potentially applied to many conifers.

10 siderable gaps deserving further research in conifers.

11 ed to initiate and mature seed crops in most conifers.

12 ing can be used to create syringyl lignin in conifers.

13 parameter range for deciduous and evergreen conifers.

14 m that can be used to study gene function in conifers.

15 atic limits among angiosperms, but not among conifers.

16 and favors broad-leaved deciduous trees over conifers.

17 extant gymnosperms, probably most closely to conifers.

18 nce was rare for the embryo lethal system in conifers.

19 Cretaceous family suggested to bark-feed on conifers.

20 urther phylogenetic and gene flow studies in conifers.

21 he genetic basis of adaptation to drought in conifers.

22 novo assembling of large genomes, such as in conifers (~ 12-30 Gbp), which also consist of ~ 80% of r

23 sperm trees and shrubs (26.3 +/- 12.4%), and conifers (7.6 +/- 2.6%).

24 ing cone size scales with branch diameter in conifers, a diverse and globally distributed lineage of

25 be mirrored by similar changes for evergreen conifers across the boreal biome.

26 stigated GS responses to increasing [CO2] of conifer and broadleaved trees in a temperate forest subj

27 moist forests and 6,825 km(2) of regrowth of conifer and dry forests.

28 of moist forests and significant recovery of conifer and dry forests.

29 ies in light of the publication of the first conifer and gymnosperm genomes.

30 the biosphere, including those of hardwood, conifer and mixed dominance, with a particular emphasis

31 tions in the United Kingdom as well as mixed conifer and oak forests in the Western United States.

32 Mean RPF was lower for both conifer and oak species with warmer dryer ranges.

33 principles previously established for ferns, conifers and angiosperms, and characterized the uniquene

34 ellulosic constituents of softwoods, such as conifers and cycads, are mannans consisting of a 1,4-lin

35 rominent constitutive terpenoids released by conifers and Eucalyptus trees on electrophysiological an

36 evolutionary context of cold acclimation in conifers and evaluate challenges imposed on them by chan

37 Within modern gymnosperms, conifers and Ginkgo are exclusively wind pollinated wher

38 rest composition toward reduced dominance of conifers and greater abundance of deciduous hardwoods, w

39 annotated transcriptomes assemblies of seven conifers and identified a resource of 3816 expressed NLR

40 sturbance resulted in the ubiquitous loss of conifers and large increases of Acer, Populus, and Querc

41 ies of mammals, birds, amphibians, reptiles, conifers and reef-building corals in 588 'trigger' sites

42 anoid resins that are now typically found in conifers and those now typically found in angiosperms ha

43 seasonal NSC dynamics were quantified for 12 conifers and three oaks along a transect spanning warm d

44 t by measuring the xylem vulnerability of 13 conifers and two short-vesseled angiosperms and comparin

45 portunity to investigate genome "obesity" in conifers and white pines.

46 Black spruce (Picea mariana, an evergreen conifer) and tamarack (Larix laricina, a deciduous conif

47 three perennial crops (alfalfa, poplar, and conifers); and four unmanaged ecosystems of different su

48 s host associations with ginkgoalean, cycad, conifer, and bennettitalean gymnosperms.

49 seeded with two widely distributed subalpine conifers, and climate manipulations replicated at three

50 tems and floras formerly dominated by ferns, conifers, and cycads.

51 toward increased hardwood composition; 2) if conifers appear stressed by recent climate change relati

52 cords are well aligned, and sedDNA of exotic conifers appears in high quantities with the establishme

53 Evergreen conifers are champions of winter survival, based on thei

54 Conifers are considered to prefer to take up ammonium (N

55 population sizes, such as widely distributed conifers, are expected to harbor relatively more DNA seq

56 umented 20(th) Century plantations of exotic conifers as an experimental system.

57 minance of deciduous hardwoods vs. evergreen conifers at different successional stages.

58 (18) O, respectively) of dying and surviving conifers at eight old-growth forest sites across a stron

59 Conifers at the alpine timberline are exposed to drought

60 tion or climate change led to the decline of conifers at the expense of angiosperms.

61 ollapse of the long-lived, endemic Tasmanian conifer Athrotaxis selaginoides in remote montane catchm

62 ions of conifer growth and to illustrate how conifers balance investments in the competing xylem func

63 trong TRPC6-inhibitory activity was found in conifer balsams.

64 nd associated microbes; and (3) implementing conifer-bark beetle interactions in current models impro

65 Three of these were orthologous to known conifer bifunctional levopimaradiene/abietadiene synthas

66 * The flow of xylem sap through conifer bordered pits, particularly through the pores in

67 late-season net photosynthesis of evergreen conifers but could also impair the development of cold h

68 n ethylene and compression wood formation in conifers, but the relationship has received no more than

69 with angiosperms increased the extinction of conifers by pushing their remaining species diversity an

70 This implies that mature conifers can adapt to increasing availability of nitrate

71 It remains unclear to what extent mature conifers can use nitrate compared to ammonium under fiel

72 on and xylem differentiation in stems of the conifer Chamaecyparis pisifera.

73 t predictor of seed size within major extant conifer clades than climate.

74 manage for the impacts of climate change on conifer cold hardiness, we conducted a common garden exp

75 imate variability, climate change may reduce conifer cold hardiness, which in turn could impact ecosy

76 changes in leaf-level physiology in a mixed conifer community that underwent significant changes in

77 s were more pronounced at drier sites, where conifers comprised a smaller portion of live woody bioma

78 temperate angiosperms, but one was a boreal conifer, contrary to predictions.

79 ulting user-friendly computational pipeline, CoNIFER (copy number inference from exome reads), can re

80 n by using available exome sequence data and CoNIFER (Copy Number Inference from Exome Reads).

81 Among extant nonflowering seed plants (conifers, cycads, Ginkgo, Gnetales), a maternally derive

82 d 20 sites in tundra, grassland, and boreal, conifer, deciduous, and tropical forest biomes using the

83 They play critical roles in conifer defense against insects and pathogens and as a r

84 t profiles of these monoterpene synthases of conifer defense against insects.

85 rt annotation of very large gene families of conifer defense metabolism, the terpene synthases and cy

86 ondary) diterpene metabolism, which produces conifer defense metabolites through variable combination

87 functional specialization relative to other conifer diTPSs.

88 ere characterized as aspen dominated, mixed, conifer dominated or open meadow, which includes the ran

89 soil nutrient concentrations than mixed and conifer dominated stands and meadows.

90 o similar levels as those found in mixed and conifer dominated stands in late summer.

91 ld have 38 times the flow resistance, making conifer-dominated ecosystems improbable in an angiosperm

92 these studies, we assess these processes in conifer-dominated forests of the Southwest United States

93 ct ecosystem functioning and productivity in conifer-dominated forests.

94 A mosaic of southern beech and conifer-dominated woodlands and tundra continued to occu

95 lethal factors are a common component of the conifer embryo lethal system.

96 Spruce (Picea spp.) and other conifers employ terpenoid-based oleoresin as part of the

97 Conifers eventually overtop the competing vegetation, bu

98 monstrate a surprising simplicity in the way conifers evolved to cope with water shortage, indicating

99 ance regimes or climate scenarios that favor conifer expansion or loss of aspen will decrease soil re

100 vents throughout the Phanerozoic and 2) that conifer extinction increased significantly in the Mid-Cr

101 Mycorrhizal root nodules occur in the conifer families Araucariaceae, Podocarpaceae, and Sciad

102 , the period during which most of the modern conifer families first appeared.

103 t diversity in habitat and morphology of any conifer family.

104 two pairs of legs); further, it establishes conifer feeding as an ancestral trait.

105 overy period, as is often observed in modern conifers following fire.

106 a correlated manner in many animal-dispersed conifers, following a trade-off that minimizes the total

107 that covers the native flowering plants and conifers for the nation of Wales (1143 species).

108 [CO2], whereas it linearly decreased for the conifer forest but was enhanced by [CO2].

109 area currently capable of supporting montane conifer forest could become subject to minimal conifer r

110 the causal factor, rather than closed canopy conifer forest exerting an effect as a barrier to disper

111 ied in riparian and upland habitat, in mixed-conifer forest habitats spanning three levels of burn se

112 aged eddy covariance data from six evergreen conifer forest sites in the semiarid western United Stat

113 nning major temperate life zones, from mixed conifer forest to high-desert grassland.

114 m thinning and burning experiment in a mixed-conifer forest to investigate the effects of the 2012-20

115 ing on plant-pollinator communities in mixed-conifer forest with frequent fire in Yosemite National P

116 ctrometer system and GPP at a winter-dormant conifer forest, which has little seasonal variation in c

117 10 and 27 months of decomposition in a mixed conifer forest.

118 soil-based metric, previously developed for conifer forests across Sweden, against the same ICP Fore

119 ite-tailed deer and were able to link use of conifer forests and agricultural fields to behavioural s

120 ng), a large wildland ecosystem dominated by conifer forests and characterized by infrequent, high-se

121 Evergreen conifer forests are the most prevalent land cover type i

122 es in spring had a positive effect on NEP in conifer forests but a negative impact in deciduous fores

123 enyltrichloroethane (DDT), to North American conifer forests during ~1950-1970.

124 Spruce-fir conifer forests have a lower optimum temperature for pho

125 ia) and drought-constrained (Spain) Eurasian conifer forests have peaked in the early 21st century at

126 GEP in conifer forests increased with higher temperature anomal

127 Results from this fire in mixed-conifer forests of California suggest that bats are resi

128 urveys of wildfire areas during 2014-2017 in conifer forests of California's Sierra Nevada Mountains.

129 bycidae, Spondylinae) is a common species in conifer forests of the Northern Hemisphere, but with glo

130 The conifer forests of this region have a long history of pr

131 nts of forest community composition in aspen-conifer forests to better understand the relationship be

132 To assess the vulnerability of conifer forests to increased fire activity and altered f

133 where severe fire initially converts montane conifer forests to systems dominated by broadleaf trees

134 and fractional canopy cover within mixed and conifer forests when leaf-on lidar data are not availabl

135 ately constrains the low-elevation extent of conifer forests within the region.

136 e the most economically important insects in conifer forests worldwide.

137 Characterized by widespread and diverse conifer forests, burning within this region may lead to

138 In conifer forests, drought had a similar dampening effect

139 oss the climatic aridity gradient of montane conifer forests.

140 the frequency of insect outbreaks in Boreal conifer forests.

141 rce for enhancing and protecting the world's conifer forests.

142 mass-showed greater drought sensitivity than conifer forests.

143 18 to 35 gigabases, sequencing even a single conifer genome had been considered unattainable until th

144 ent of gene and pseudogene duplications in a conifer genome, in particular for genes of secondary (i.

145 enced plant genomes, including a much larger conifer genome, the Ae. tauschii genome contains unprece

146 milies of up to a dozen different members in conifer genomes and fall into four different clades (I-I

147 specific range of noncanonical DNA bases in conifer genomes implying potential roles for these modif

148 ives have been launched recently to sequence conifer genomes including pines, spruces and Douglas-fir

149 larch species in addition to only five other conifer genomes sequenced and assembled for Picea abies,

150 mbly enabled the recent publication of three conifer genomes: white spruce (Picea glauca), Norway spr

151 nce and provide a reference resource for the conifer genomics community.

152 the assembly of very large genomes, and the conifer genomics resources developed in this process.

153 as been established as one of the models for conifer genomics.

154 scale classification of deep lineages of the conifer genus Picea, establish their phylogenetic relati

155 ven between deeply branching lineages of the conifer genus Picea.

156 Conifer, Gingko, and Cycad xylan lacks acetylation but i

157 cell walls of the four gymnosperm lineages (Conifer, Gingko, Cycad, and Gnetophyta).

158 rved across diverse lineages (ferns, cycads, conifers, ginkgo, basal angiosperms, magnoliids, monocot

159 using distinct plant substrates (angiosperm, conifer, grass).

160 d understanding of interannual variations of conifer growth and to illustrate how conifers balance in

161 g the growing season could negatively impact conifer growth, indicating possible seasonal climate wat

162 plete characterization of the megagenomes of conifers has remained elusive.

163 , an ecologically and economically important conifer, has a large and yet uncharacterized genome of 2

164 We showed that conifers have among the most diverse and numerous RNLs i

165 To survive harsh winter conditions, conifers have evolved a unique but poorly characterized

166 any evident signal of gbM within exons, but conifers have high levels of both CG and CHG (where H is

167 ic, transcriptomic and metabolomic tools for conifers have improved our understanding of how trees se

168 Conifers have potent defenses, but resistance to beetles

169 t genome sequences of white spruce and other conifers have recently been produced, but dense genetic

170 e most widespread and economically important conifer in Europe.

171 Evergreen conifers in boreal forests can survive extremely cold (f

172 Coping of evergreen conifers in boreal forests with freezing temperatures on

173 hat fungal diseases are a growing menace for conifers in modern silviculture, only a very limited num

174 Increased dispersal limitation of evergreen conifers, in turn, is predicted to increase the prevalen

175 Bordered pits of many conifers include a torus-margo structure acting as a val

176 ovel way of understanding bark beetle-fungal-conifer interactions.

177 Economically important softwood from conifers is mainly composed of the polysaccharides cellu

178 unctional trait and environmental proxy - in conifers is poorly understood.

179 e regimes, dispersal limitation of evergreen conifers is predicted to become more severe, primarily d

180 The flow of xylem sap in conifers is strongly dependent on the presence of a low

181 limation and cold hardiness in overwintering conifers, leading to cessation of growth, bud dormancy,

182 ient at abstracting electrons from softwood (conifer) lignin.

183 fication models in which Northern Hemisphere conifer lineages have higher rates of species turnover t

184 r fireline intensities than those fuelled by conifer litter or weedy angiosperms, and whilst fern und

185 on in analogue Cretaceous understorey fuels (conifer litter, ferns, weedy and shrubby angiosperms) an

186 C starvation was a strong correlate of conifer mortality based on a conceptual model incorporat

187 Conifer mortality rates are increasing in western North

188 detected in 100% of the PM2.5 emissions from conifers (n=11), 94% of emissions from agricultural resi

189 thods and are influenced by vegetation type (conifer needle, deciduous simple leaf or deciduous compo

190 er consuming cambial and wood tissues of the conifer Ningxiaites specialis.

191 Conifers normally go through a long juvenile period, for

192 thm, is critical for local adaptation of the conifer Norway spruce (Picea abies).

193 in non-negligible quantities in the DNA of a conifer, Norway spruce.

194 llularly preserved root nodules of the early conifer Notophytum from Middle Triassic permineralized p

195 r formed from resins exuded by cupressaceous conifers occupying a coastal plain.

196 Water transport in conifers occurs through single-celled tracheids that are

197 edge foundation has been acquired in several conifers of commercial and ecological interest through l

198 eeds and seedlings of western North American conifers of different origin populations into different

199 Conifers of the pine family (Pinaceae) are a group of gy

200 s (DRAs), which are a major component of the conifer oleoresin defense system.

201 clades produce some of the same profiles of conifer oleoresin DRAs (abietic acid, neoabietic acid, l

202 The success of conifers over much of the world's terrestrial surface is

203 arvae of the nun moth (Lymantria monacha), a conifer pest in Eurasia.

204 an which studied the widespread thermophilic conifer Pinus halepensis and involved 157 populations ca

205 cross a range of xylem pressures (Px) in the conifers Pinus contorta and Juniperus scopulorum.

206 ence of logging, we found a diverse suite of conifers (Pinus, Abies, Juniperus, Picea, and Larix) str

207 g to the unique torus-margo structure of the conifer pit membrane.

208 ures of a mixed native species plantation, a conifer plantation and an Acacia mangium plantation in S

209 ed areas, suggesting that fuel conditions in conifer plantations can increase fire severity despite r

210 e value of heathland areas within commercial conifer plantations with regards to their future managem

211 was subject, in part, to salvage-logging and conifer planting before it reburned during the 2002 Bisc

212 during leaf-off periods except in mixed and conifer plots; and 4) depth of laser pulse penetration l

213 regeneration of two dominant, low-elevation conifers (ponderosa pine and Douglas-fir) using annually

214 The evolutionary history of conifers provides an opportunity to explore these dynami

215 Recently documented declines in postfire conifer recruitment in the western United States may be

216 Postfire conifer recruitment was limited to a narrow window, with

217 e drought have emerged as key constraints on conifer recruitment.

218 We present data from a study of early conifer regeneration and fuel loads after the 2002 Biscu

219 nifer forest could become subject to minimal conifer regeneration in even moderate-sized (10s of ha)

220 Natural conifer regeneration was abundant after the high-severit

221 rcodes for Welsh native flowering plants and conifers represents the most complete coverage of any na

222 y, methyl jasmonate (MJ) was shown to induce conifer resin and phenolic defenses; however, it is not

223 etane diterpenoids are major constituents of conifer resins that have important industrial and medici

224 The conifer RNL repertoire harbours four distinct groups, wi

225 icates that mutualistic associations between conifer root nodules and arbuscular mycorrhizal fungi da

226 Conifer RPF variability was explained by environment, in

227 severity fire) was needed to support a given conifer seedling density, which implies that projected f

228 models, we investigated the colonization of conifer seedling roots in vitro using an array of 201 ba

229 te their ecological and economic importance, conifers seemed long out of reach for complete genome se

230 Conifers (softwoods) naturally lack syringyl units in th

231 ol model, we examined stomatal behavior in a conifer species (Metasequoia glyptostroboides) that is p

232 a sempervirens) is one of just two polyploid conifer species and the only hexaploid.

233 ese dynamics, because the majority of extant conifer species belong to lineages that have been broadl

234 Most extant conifer species diverged recently during the Neogene wit

235 longevity in two natural populations of the conifer species Pinus ponderosa Hydraulic constraints ar

236 one of the main Siberian boreal forest tree conifer species Siberian larch (Larix sibirica Ledeb.) a

237 ecovery of these important central Europe to conifer species the exceptional droughts in 1976 and 200

238 ing recruitment and tree-ring data from four conifer species to assess: 1) whether the forest appears

239 e observed intra-annual growth rates of four conifer species using point dendrometers and microcores,

240 a plicata (western redcedar) is a long-lived conifer species whose foliage is rarely affected by dise

241 tion of water stress on two drought-tolerant conifer species with contrasting stomatal behavior.

242 trait evolution for a data set of 293 extant conifer species within an explicit phylogenetic framewor

243 Using Taxus baccata, a conifer species without resin, we developed a modified r

244 er is a strong predictor of cone size across conifer species, particularly for pollen cones and dry s

245 es CYP720B2 and CYP720B12 in three different conifer species, Sitka spruce, lodgepole pine (Pinus con

246 r pathogen resistance have been validated in conifer species.

247 shoot growth of mature trees of two semiarid conifer species.

248 America and Mexico contain a large number of conifer species.

249 ylogeny sampling approximately 80% of living conifer species.

250 ent with persistence of the current suite of conifer species.

251 and Df to model the freeze-thaw response in conifer species.

252 Gs) with localization on homologousLGs among conifer species.

253 lates to the growth-longevity trade-off in a conifer species.

254 We use the reproductive cones of conifers, specifically the Pinaceae clade, to explore th

255 pth analysis of the sRNA population from the conifer spruce (Picea abies) and compared the results wi

256 aily gross primary productivity of evergreen conifer stands measured by eddy covariance.

257 as significantly higher in aspen stands than conifer stands or meadows throughout the summer.

258 Conifer stem pest resistance includes constitutive defen

259 Rapidly enhancing oleoresin production in conifer stems through genomic selection and genetic engi

260 ss inducible defense signaling mechanisms in conifer stems.

261 rength of these scaling relationships across conifers suggest that reproductive and vegetative morpho

262 tance in the curiously overbuilt New Zealand conifers suggests that their xylem properties may be mor

263 s (unaltered natural products) in the fossil conifers supports their systematic assignment to the Cyp

264 nt role in the speciation and persistence of conifer taxa in diversity hotspots, by providing diverse

265 le pine (Pinus contorta subsp. latifolia), a conifer that dominates millions of hectares in western N

266 lodgepole pine, a widespread North American conifer that is also planted globally.

267 upressoides is a slow-growing and long-lived conifer that occurs in the subalpine temperate forests o

268 idth measurement series from living and dead conifers that grew in undisturbed, high-elevation sites

269 Of various conifers, the larch balsam was unique in displaying a ma

270 by animals in the evolution of seed size in conifers, the most diverse extant nonflowering seed plan

271 However, in the leaves of conifers, the reversible collapse of transfusion trachei

272 Intragenic LD decays rapidly in conifers; thus SNPs showing genetic association are like

273 e physiological mechanisms used by evergreen conifers to adjust metabolism seasonally and to protect

274 measurements of hundreds of living and dead conifers to reconstruct the impact of heavy industrialis

275 nd physiological evidence from 42 species of conifers to show that the evolution of drought resistanc

276 The unicellular conifer tracheid should have greater flow resistance per

277 to the 56% in angiosperm vessels and 64% in conifer tracheids.

278 We found population size structures for most conifer tree species to be consistent with self-replacem

279 complex inner mechanisms that create typical conifer tree-ring structure (i.e. the transition from la

280 sults show that the formation of the typical conifer tree-ring structure, in normal climatic conditio

281 relation to associated climatic variables in conifers - treeline-dominant Pinus albicaulis had the lo

282 on how drought affects interactions between conifer trees and bark beetles.

283 zygous and long-lived such as in the case of conifer trees.

284 TX, TN and TNL proteins were demonstrated in conifers; TX and TN genes are present in very low number

285 ate and cone morphology were analyzed across conifers using quantitative models of character evolutio

286 indicate that this fire-sensitive Gondwanan conifer was able to persist with burning by Aboriginal T

287 the modern biogeography of the Cupressaceae conifers was shaped in large part by their capacity to a

288 show that dispersal limitation of evergreen conifers was the main factor determining postfire regene

289 s, birds, selected reptiles, amphibians, and conifers), we find 794 such species, three times the num

290 time trees and vetted fossil occurrences for conifers, we tested the hypotheses that clade competitio

291 r) and tamarack (Larix laricina, a deciduous conifer) were grown under ambient (407 ppm) or elevated

292 rsifying microhabitats (admixing of oaks and conifers) were important and mostly affected richness.

293 is of particular utility in species such as conifers, where genomewide strategies are limited by the

294 In evergreen conifers, where the foliage amount changes little with s

295 enomic resources have been developed for the conifer white spruce (Picea glauca, Pinaceae), which has

296 rmation are primarily composed of comminuted conifer wood tissues that were fungally degraded before

297 inus sylvestris) is one of the most abundant conifers worldwide, and evidence is rising that its resi

298 gi are among the greatest natural threats to conifers worldwide.

299 Without their specialized pits, conifers would have 38 times the flow resistance, making

300 s support the stable binding of 2-fold screw conifer xylan to the hydrophilic face of cellulose micro