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1 an approximation-based methods (e.g. XHMM or CoNIFER).
2 m that can be used to study gene function in conifers.
3 he genetic basis of adaptation to drought in conifers.
4 and favors broad-leaved deciduous trees over conifers.
5 extant gymnosperms, probably most closely to conifers.
6 nce was rare for the embryo lethal system in conifers.
7 ant part in the lag in flow observed in many conifers.
8 icots; and arborescent monocots, dicots, and conifers.
9 ng selfing rates are thought to be absent in conifers.
10 e genetic mechanism promoting outcrossing in conifers.
11 ad a close relationship between Gnetales and conifers.
12 ally and chloroplasts paternally, as in many conifers.
13 enetic conservation and breeding programs in conifers.
14 oncern that it may also kill pines and other conifers.
15 s may contribute to the large genome size of conifers.
16 allitris, the world's most drought-resistant conifers.
17 ng role of aridity in the diversification of conifers.
18 ial variation in the density of regenerating conifers.
19 ly stable N2 -fixing strategy for long-lived conifers.
20 lowest of all in streams draining non-native conifers.
21 ic and respiratory fluxes from high-latitude conifers.
22 is method can be potentially applied to many conifers.
23 ed to initiate and mature seed crops in most conifers.
24 ing can be used to create syringyl lignin in conifers.
26 ing cone size scales with branch diameter in conifers, a diverse and globally distributed lineage of
27 stigated GS responses to increasing [CO2] of conifer and broadleaved trees in a temperate forest subj
31 the biosphere, including those of hardwood, conifer and mixed dominance, with a particular emphasis
32 principles previously established for ferns, conifers and angiosperms, and characterized the uniquene
33 ellulosic constituents of softwoods, such as conifers and cycads, are mannans consisting of a 1,4-lin
35 ns of beetle-fungal complexes with live host conifers and determining the ecological advantages for m
36 rominent constitutive terpenoids released by conifers and Eucalyptus trees on electrophysiological an
38 rest composition toward reduced dominance of conifers and greater abundance of deciduous hardwoods, w
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 t by measuring the xylem vulnerability of 13 conifers and two short-vesseled angiosperms and comparin
45 of the regulation of oleoresin formation in conifers and will ultimately permit the transgenic manip
46 three perennial crops (alfalfa, poplar, and conifers); and four unmanaged ecosystems of different su
48 seeded with two widely distributed subalpine conifers, and climate manipulations replicated at three
50 for land plants reveals that mosses, ferns, conifers, and flowering plants have similar percentages
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 Scolytid bark beetles that colonize living conifers are frequently associated with specific fungi t
54 population sizes, such as widely distributed conifers, are expected to harbor relatively more DNA seq
59 ions of conifer growth and to illustrate how conifers balance investments in the competing xylem func
61 Three of these were orthologous to known conifer bifunctional levopimaradiene/abietadiene synthas
63 late-season net photosynthesis of evergreen conifers but could also impair the development of cold h
64 n ethylene and compression wood formation in conifers, but the relationship has received no more than
67 manage for the impacts of climate change on conifer cold hardiness, we conducted a common garden exp
68 imate variability, climate change may reduce conifer cold hardiness, which in turn could impact ecosy
69 changes in leaf-level physiology in a mixed conifer community that underwent significant changes in
70 s were more pronounced at drier sites, where conifers comprised a smaller portion of live woody bioma
72 ulting user-friendly computational pipeline, CoNIFER (copy number inference from exome reads), can re
75 d 20 sites in tundra, grassland, and boreal, conifer, deciduous, and tropical forest biomes using the
78 rt annotation of very large gene families of conifer defense metabolism, the terpene synthases and cy
79 ondary) diterpene metabolism, which produces conifer defense metabolites through variable combination
80 ase, interactions with preformed and induced conifer defenses, or the combined action of both beetles
81 enoid synthase gene resembled a contemporary conifer diterpene synthase gene in containing at least 1
83 ere characterized as aspen dominated, mixed, conifer dominated or open meadow, which includes the ran
86 ld have 38 times the flow resistance, making conifer-dominated ecosystems improbable in an angiosperm
87 these studies, we assess these processes in conifer-dominated forests of the Southwest United States
91 f gene expression during the early stages of conifer embryogenesis, we identified a transcript, PtNIP
95 monstrate a surprising simplicity in the way conifers evolved to cope with water shortage, indicating
96 ance regimes or climate scenarios that favor conifer expansion or loss of aspen will decrease soil re
102 a correlated manner in many animal-dispersed conifers, following a trade-off that minimizes the total
105 area currently capable of supporting montane conifer forest could become subject to minimal conifer r
106 the causal factor, rather than closed canopy conifer forest exerting an effect as a barrier to disper
107 ied in riparian and upland habitat, in mixed-conifer forest habitats spanning three levels of burn se
108 he past few decades, the planting of a large conifer forest has connected groups of forest fragments
109 ing on plant-pollinator communities in mixed-conifer forest with frequent fire in Yosemite National P
111 ite-tailed deer and were able to link use of conifer forests and agricultural fields to behavioural s
112 ng), a large wildland ecosystem dominated by conifer forests and characterized by infrequent, high-se
114 ia) and drought-constrained (Spain) Eurasian conifer forests have peaked in the early 21st century at
117 nts of forest community composition in aspen-conifer forests to better understand the relationship be
119 where severe fire initially converts montane conifer forests to systems dominated by broadleaf trees
120 and fractional canopy cover within mixed and conifer forests when leaf-on lidar data are not availabl
125 18 to 35 gigabases, sequencing even a single conifer genome had been considered unattainable until th
126 ent of gene and pseudogene duplications in a conifer genome, in particular for genes of secondary (i.
127 enced plant genomes, including a much larger conifer genome, the Ae. tauschii genome contains unprece
128 milies of up to a dozen different members in conifer genomes and fall into four different clades (I-I
129 ives have been launched recently to sequence conifer genomes including pines, spruces and Douglas-fir
130 mbly enabled the recent publication of three conifer genomes: white spruce (Picea glauca), Norway spr
132 the assembly of very large genomes, and the conifer genomics resources developed in this process.
139 d understanding of interannual variations of conifer growth and to illustrate how conifers balance in
140 g the growing season could negatively impact conifer growth, indicating possible seasonal climate wat
142 , an ecologically and economically important conifer, has a large and yet uncharacterized genome of 2
143 any evident signal of gbM within exons, but conifers have high levels of both CG and CHG (where H is
145 t genome sequences of white spruce and other conifers have recently been produced, but dense genetic
147 hat fungal diseases are a growing menace for conifers in modern silviculture, only a very limited num
148 or studying defensive oleoresin formation in conifers in response to insect attack or other injury.
149 Increased dispersal limitation of evergreen conifers, in turn, is predicted to increase the prevalen
151 defined here is conserved in liverworts and conifers, indicating that the phage-type transcription m
154 e regimes, dispersal limitation of evergreen conifers is predicted to become more severe, primarily d
158 fication models in which Northern Hemisphere conifer lineages have higher rates of species turnover t
159 r fireline intensities than those fuelled by conifer litter or weedy angiosperms, and whilst fern und
160 on in analogue Cretaceous understorey fuels (conifer litter, ferns, weedy and shrubby angiosperms) an
161 synthases and diterpene (C20) synthases from conifers more closely than other monoterpene synthases f
162 detected in 100% of the PM2.5 emissions from conifers (n=11), 94% of emissions from agricultural resi
163 thods and are influenced by vegetation type (conifer needle, deciduous simple leaf or deciduous compo
167 llularly preserved root nodules of the early conifer Notophytum from Middle Triassic permineralized p
169 edge foundation has been acquired in several conifers of commercial and ecological interest through l
170 eeds and seedlings of western North American conifers of different origin populations into different
173 clades produce some of the same profiles of conifer oleoresin DRAs (abietic acid, neoabietic acid, l
175 , surprisingly, that Gnetales are related to conifers, or even derived from them, and that no other e
179 genomic clones encoding terpene synthases of conifers, [(-)-pinene (C(10)), (-)-limonene (C(10)), (E)
181 ence of logging, we found a diverse suite of conifers (Pinus, Abies, Juniperus, Picea, and Larix) str
183 ures of a mixed native species plantation, a conifer plantation and an Acacia mangium plantation in S
184 ed areas, suggesting that fuel conditions in conifer plantations can increase fire severity despite r
185 e value of heathland areas within commercial conifer plantations with regards to their future managem
186 was subject, in part, to salvage-logging and conifer planting before it reburned during the 2002 Bisc
187 during leaf-off periods except in mixed and conifer plots; and 4) depth of laser pulse penetration l
191 nifer forest could become subject to minimal conifer regeneration in even moderate-sized (10s of ha)
193 rcodes for Welsh native flowering plants and conifers represents the most complete coverage of any na
194 y, methyl jasmonate (MJ) was shown to induce conifer resin and phenolic defenses; however, it is not
195 etane diterpenoids are major constituents of conifer resins that have important industrial and medici
196 icates that mutualistic associations between conifer root nodules and arbuscular mycorrhizal fungi da
197 severity fire) was needed to support a given conifer seedling density, which implies that projected f
198 models, we investigated the colonization of conifer seedling roots in vitro using an array of 201 ba
199 te their ecological and economic importance, conifers seemed long out of reach for complete genome se
202 ol model, we examined stomatal behavior in a conifer species (Metasequoia glyptostroboides) that is p
204 ese dynamics, because the majority of extant conifer species belong to lineages that have been broadl
206 ecovery of these important central Europe to conifer species the exceptional droughts in 1976 and 200
207 ing recruitment and tree-ring data from four conifer species to assess: 1) whether the forest appears
208 e observed intra-annual growth rates of four conifer species using point dendrometers and microcores,
209 a plicata (western redcedar) is a long-lived conifer species whose foliage is rarely affected by dise
210 tion of water stress on two drought-tolerant conifer species with contrasting stomatal behavior.
211 trait evolution for a data set of 293 extant conifer species within an explicit phylogenetic framewor
213 er is a strong predictor of cone size across conifer species, particularly for pollen cones and dry s
214 es CYP720B2 and CYP720B12 in three different conifer species, Sitka spruce, lodgepole pine (Pinus con
224 pth analysis of the sRNA population from the conifer spruce (Picea abies) and compared the results wi
228 Rapidly enhancing oleoresin production in conifer stems through genomic selection and genetic engi
230 rength of these scaling relationships across conifers suggest that reproductive and vegetative morpho
231 s (unaltered natural products) in the fossil conifers supports their systematic assignment to the Cyp
232 nt role in the speciation and persistence of conifer taxa in diversity hotspots, by providing diverse
233 tural product terpenoids found in two fossil conifers, Taxodium balticum (Eocene) and Glyptostrobus o
234 le pine (Pinus contorta subsp. latifolia), a conifer that dominates millions of hectares in western N
236 upressoides is a slow-growing and long-lived conifer that occurs in the subalpine temperate forests o
238 by animals in the evolution of seed size in conifers, the most diverse extant nonflowering seed plan
241 nd physiological evidence from 42 species of conifers to show that the evolution of drought resistanc
244 however, large-scale use of this organism in conifer transformation has been limited by difficult pro
245 We found population size structures for most conifer tree species to be consistent with self-replacem
246 complex inner mechanisms that create typical conifer tree-ring structure (i.e. the transition from la
247 sults show that the formation of the typical conifer tree-ring structure, in normal climatic conditio
248 Between A.D. 900 and 1150, more than 200,000 conifer trees were used to build the prehistoric great h
250 TX, TN and TNL proteins were demonstrated in conifers; TX and TN genes are present in very low number
251 ate and cone morphology were analyzed across conifers using quantitative models of character evolutio
252 ons are insensitive to phyletic affiliation (conifers versus angiosperms) and variation in averaged l
253 the modern biogeography of the Cupressaceae conifers was shaped in large part by their capacity to a
254 show that dispersal limitation of evergreen conifers was the main factor determining postfire regene
255 s, birds, selected reptiles, amphibians, and conifers), we find 794 such species, three times the num
256 is of particular utility in species such as conifers, where genomewide strategies are limited by the
258 enomic resources have been developed for the conifer white spruce (Picea glauca, Pinaceae), which has
259 rmation are primarily composed of comminuted conifer wood tissues that were fungally degraded before
262 s support the stable binding of 2-fold screw conifer xylan to the hydrophilic face of cellulose micro
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