ライフサイエンスコーパス: spruce

1 riana (black spruce) and Picea glauca (white spruce).

2 orth American forest insect pest of pine and spruce.

3 ative-to-reproductive phase change in Norway spruce.

4 oncert to control perennial growth in Norway spruce.

5 ative-to-reproductive phase change in Norway spruce.

6 TR sequences from pea, broad bean and Norway spruce.

7 ree was up to 11 mg for birch and 1.8 mg for spruce.

8 discrimination and growth of black and white spruce.

9 nt-wide masting in European beech and Norway spruce.

10 glycosylated acetophenone pungenin in white spruce.

11 ne, portends range contraction for Engelmann spruce.

12 needles across different genotypes of white spruce.

13 an unstructured natural population of Norway spruce.

14 related species, lodgepole pine and interior spruce.

15 compensatory cis-trans factors is common in spruce.

16 Norway spruce accumulates high foliar concentrations of seconda

17 y enable marker-assisted selection of Norway spruce adapted to severe pathogen attack.

18 arene is associated with resistance of Sitka spruce against white pine weevil, a major North American

19 with the synthesis of the natural products, spruce alkaloid and (+)-241D.

20 e, and yellow birch, and negatively with red spruce and balsam fir - generally more so for adults tha

21 e climates is likely to become a problem for spruce and beech by the end of this century, but probabl

22 ies should be adjusted in the study area for spruce and beech to maintain productive and healthy fore

23 ee climate models, future risks increased in spruce and beech until the end of the century, but remai

24 Case studies with European beech, Qinghai spruce and Douglas-fir illustrate how the combination of

25 large-scale generation of transgenic Norway spruce and may prove useful for other conifer species.

26 Draft genome sequences of white spruce and other conifers have recently been produced, b

27 s included mature black spruce, burned black spruce and paper birch, allowing us to determine vegetat

28 Here, we leverage the Spruce and Peatland Responses Under Changing Environment

29 ciency of heterologous hybridization between spruce and pine species on microarrays has been document

30 nt resistance mechanism against SBW in white spruce and that insects can affect population structure

31 to sequence conifer genomes including pines, spruces and Douglas-fir.

32 from stems and roots of Picea mariana (black spruce) and Picea glauca (white spruce).

33 Thus, white spruce apparently survived long glacial episodes under c

34 ol of growth cessation and bud set in Norway spruce as well as in local adaptation resulting in clina

35 gnocellulosic biomass, namely, beech, birch, spruce, ash, oak, and pine as well as commercial availab

36 dominant forest types (paper birch and black spruce) associated with location on elevated permafrost

37 of polymerization increased dramatically in spruce bark after infection by C. polonica.

38 ca, a phytopathogenic fungus vectored by the spruce bark beetle Ips typographus.

39 ed changes in the phenolic content of Norway spruce bark upon E. polonica infection and the biochemic

40 group of phenolic compounds found in Norway spruce bark with a diaryl-ethene skeleton with known ant

41 h 2,3-trans stereochemistry were detected in spruce bark; dimeric and larger PAs contained flavan-3-o

42 ine beetle (Dendroctonus ponderosae) and the spruce beetle (D. rufipennis) have recently undergone ep

43 e against the insect but can be cleaved by a spruce beta-glucosidase, PgbetaGLU-1, which releases the

44 ugh the total quantity of C emitted from the SPRUCE Bog as CH4 is <2%, CH4 represents >50% of seasona

45 teristic of interior Alaska, including black spruce, bog birch, tussock grass and two fens.

46 ng over a developmental time course of white spruce bud burst and shoot growth revealed two UGTs, PgU

47 tance of white spruce (Picea glauca) against spruce budworm (Choristoneura fumiferiana), a major fore

48 AFPs from overwintering insects, such as the spruce budworm (sbw) are 10-100 times more effective tha

49 tion between white spruce (Picea glauca) and spruce budworm (SBW, Choristoneura fumiferana) the most

50 The spruce budworm AFP lacks regular repeat units.

51 virion protein extract induces apoptosis in spruce budworm and cotton boll weevil cell cultures.

52 a-solenoid protein mutant fibril structures (spruce budworm and Rhagium inquisitor antifreeze protein

53 based on the primary sequence of the mature spruce budworm antifreeze protein (sbwAFP) was construct

54 protein structure-function mechanism for the spruce budworm Choristoneura fumiferana AFP, including s

55 d length-to-width correlation for the mutant spruce budworm protein and the resultant UTS estimate is

56 ism by which the antifreeze protein from the spruce budworm, Choristoneura fumiferana, binds to ice.

57 Our sites included mature black spruce, burned black spruce and paper birch, allowing us

58 ilarly to warming across sites for Engelmann spruce, but differently for limber pine.

59 The vast majority of sRNA sequences in spruce can be assigned to 21-nucleotide-long siRNA seque

60 t, many conifers, including pines, firs, and spruces, can accumulate chlorophyll and the light-harves

61 tland Responses Under Changing Environments (SPRUCE) climate change manipulation experiment to unders

62 ses of boreal forest recovery from prior red spruce decline, or human land use and disturbance, may s

63 likely the first steps in the degradation of spruce defenses to substrates that can enter the tricarb

64 RNA extracted from maturing spruce embryos was analyzed on DNA microarrays containin

65 thwest Alaska to explore factors influencing spruce establishment and recruitment near western treeli

66 e abundance suggests a moving front of white spruce establishment through time, driven by changes in

67 eriments wood chips of oak, poplar, hickory, spruce, fir, alder, beech, and beech with an apple-smoki

68 Spruce-fir conifer forests have a lower optimum temperat

69 ing the transition from northern hardwood to spruce-fir forests.

70 ing the transition from northern hardwood to spruce-fir forests.

71 deciduous/hardwood forest (14.1 mug/m2-yr), spruce/fir forest (33.8 mug/m2-yr), and stunted growth a

72 ion hardwoods to throughfall in midelevation spruce/fir to cloudwater in high-elevation alpine forest

73 s pungenol and piceol commonly accumulate in spruce foliage in the form of the corresponding glycosid

74 forests and a relatively continuous gain of spruce forest associated with thermokarst and forest suc

75 as the primary factors controlling birch and spruce forest change, respectively.

76 dioxide (CO2) flux were measured at a black spruce forest in interior Alaska using the eddy covarian

77 e the carbon balance of a 120-year-old black spruce forest in Manitoba, Canada.

78 ck tundra), as well as ecotonal boreal white spruce forest, and perform model simulations for the yea

79 genome assembly and introduce a second white spruce genome assembly for genotype WS77111.

80 -scale assembly of the next-generation white spruce genome sequence and provide a reference resource

81 Although the current white spruce genome sequence remains highly fragmented, dozens

82 7111 genomes confirm the reconstructed white spruce genome size in the 20 Gbp range, and show broad s

83 ng the PG29 V3 assembly and additional white spruce genomics and transcriptomics resources, we perfor

84 espectively, resistant and susceptible Sitka spruce genotypes are due to variation of (+)-3-carene sy

85 The two white spruce genotypes originate from distant geographic regio

86 ibe the draft genome assemblies of two white spruce genotypes, PG29 and WS77111, innovative tools for

87 rticularly high frequencies were observed in spruce, grape (Vitis vinifera), and poplar (Populus tric

88 In this study, we examined patterns of black spruce growth and carbon isotopic composition in tree ri

89 atitudinal shift in the correlation of black spruce growth with temperature and reduced precipitation

90 ggest drought is causing a decline in boreal spruce growth, leading to predictions of widespread mort

91 Plots with Norway spruce had the highest net accumulation of Cl(-) and Clo

92 ite, Western redcedar, Baldcypress, and Blue spruce) had median MAC values ranging from 1.4 x 10(-2)

93 Exploratory sequencing in pines and spruces have pointed out some of the unique properties o

94 Douglas fir and Norway spruce, however, revealed lower drought resilience at hi

95 terpenoids, we overexpressed a bifunctional spruce IDS, a geranyl diphosphate and geranylgeranyl dip

96 es C/EC seedlings and lowest in +8 degrees C spruce, implying that moderate, but not extreme, climate

97 system with mixed stands of silver birch and spruce in combination with regular harvest of leaves and

98 position) from 20 productive stands of white spruce in the interior of Alaska.

99 nhabiting mycobiomes, at least not for white spruce in this extreme environment.

100 ; the presence of a least preferred species (spruce) in a mixture had no significant effect on moose

101 ct (+)-3-carene synthase-like genes of Sitka spruce include the three (+)-3-carene synthases, PsTPS-3

102 ion of phenolic needle metabolites in Norway spruce is regulated by many genes with small and additiv

103 ney samples and honeydew honeys from fir and spruce it was absent.

104 flavan-3-ols, transcript abundance of Norway spruce LEUCOANTHOCYANIDIN REDUCTASE genes also increased

105 diminished by the fourth year for Engelmann spruce, likely due to small sample sizes.

106 12 in three different conifer species, Sitka spruce, lodgepole pine (Pinus contorta), and jack pine (

107 st (in fens) to some of the lowest (in black spruce) measured globally.

108 We also comprehensively annotated the white spruce mevalonate, methylerythritol phosphate and phenyl

109 for American beech, downslope shifts for red spruce (more so in cool regions) and sugar maple, and no

110 from inbred crosses of a naturally occurring spruce mutant (acrocona).

111 (ww) and 94 ng g(-1) ww in birch leaves and spruce needles, respectively.

112 E. polonica utilization of the most abundant spruce phenolics as carbon sources both correlated posit

113 eech (Fagus sylvatica) and coniferous Norway spruce (Picea abies Karst), planted in the same soil.

114 of Scots pine (Pinus sylvestris L.), Norway spruce (Picea abies L.), Siberian larch (Larix sibirica

115 ysis of the sRNA population from the conifer spruce (Picea abies) and compared the results with those

116 seed plants, including the gymnosperm Norway spruce (Picea abies) and the angiosperms rice (Oryza sat

117 ically important tree species such as Norway spruce (Picea abies) are required, if the frequency and

118 o through a long juvenile period, for Norway spruce (Picea abies) around 20 to 25 years, before devel

119 Norway spruce (Picea abies) forests suffer periodic fatal attac

120 y identified in birch (Betula verrucosa) and spruce (Picea abies) GX.

121 Norway spruce (Picea abies) is periodically attacked by the bar

122 root formation and nutrient uptake by Norway spruce (Picea abies) seedlings with fast- and slow-growi

123 along hillslopes in four 80 years old Norway spruce (Picea abies) stands (REFs) with those in four si

124 tudy indicated that the resistance of Norway spruce (Picea abies) to Heterobasidion annosum s.l., a p

125 Norway spruce (Picea abies) trees (approximately 16 m high) of

126 llular lignin-forming cell culture of Norway spruce (Picea abies) was used as a research model.

127 CO2 impacted leaf carbon dynamics in Norway spruce (Picea abies), a dominant northern forest species

128 genomes: white spruce (Picea glauca), Norway spruce (Picea abies), and loblolly pine (Pinus taeda).

129 namely silver birch (Betula pendula), Norway spruce (Picea abies), bird cherry (Prunus padus), mounta

130 in three major European tree species, Norway spruce (Picea abies), silver fir (Abies alba), and Europ

131 ied and functionally characterized in Norway spruce (Picea abies), the most widespread and economical

132 nteraction with cellulose surfaces in Norway spruce (Picea abies).

133 l for local adaptation of the conifer Norway spruce (Picea abies).

134 nd characterization of the gymnosperm Norway spruce (Picea abies, Pa) ESP.

135 fossil needles that a now-extinct species of spruce (Picea critchfieldii sp. nov.) was widespread in

136 the prospect of implementing GS for interior spruce (Picea engelmannii x glauca) utilizing a genotype

137 ompounds involved in the resistance of white spruce (Picea glauca) against spruce budworm (Choristone

138 d the antagonistic interaction between white spruce (Picea glauca) and spruce budworm (SBW, Choriston

139 sequences from the needle mycobiome of white spruce (Picea glauca) at the northern treeline in Alaska

140 ed tissues of a single self-fertilized white spruce (Picea glauca) individual to dissect eQTLs accord

141 ructure and environmental data from 95 white spruce (Picea glauca) plots sampled across a longitudina

142 Somatic embryogenic cultures of white spruce (Picea glauca) represent a valuable system to stu

143 geranylgeranyl diphosphate synthase in white spruce (Picea glauca) saplings.

144 e sequenced chloroplast DNA (cpDNA) of white spruce (Picea glauca), a dominant boreal tree species, i

145 White spruce (Picea glauca), a gymnosperm tree, has been estab

146 nvestigated transcriptome structure in white spruce (Picea glauca), aiming to delineate its modular o

147 publication of three conifer genomes: white spruce (Picea glauca), Norway spruce (Picea abies), and

148 es have been developed for the conifer white spruce (Picea glauca, Pinaceae), which has one of the la

149 ed on the geometry of bordered pits in black spruce (Picea mariana) and scanning electron microscopy

150 olly pine (Pinus taeda) PtCYP720B1 and Sitka spruce (Picea sitchensis) PsCYP720B4, have been characte

151 Spruce (Picea spp.) and other conifers employ terpenoid-

152 More than one-fifth of these timbers were spruce (Picea) or fir (Abies) that were hand-carried fro

153 3 years for three coniferous species (Norway spruce [Picea abies], Scots pine [Pinus sylvestris], and

154 crobes, and roots) over 18 months in a Sitka spruce plantation and directly compared the fate of this

155 Norway spruce plants carrying at least one copy of the novel al

156 Oak, Western redcedar, and Blue spruce possessed statistically similar (p > 0.05) spectr

157 id products accepting a wide range of Norway spruce-produced phenolics as substrates.

158 Norway spruce produces terpenoid resins and phenolics in respon

159 Norway spruce protects itself against fungal and bark beetle in

160 We found that black spruce radial growth responded negatively to monthly met

161 y to expectations, warming reduced Engelmann spruce recruitment at and above treeline, as well as in

162 olar death in the embryo suspensor of Norway spruce requires autophagy.

163 Our haploid-diploid eQTL analysis in spruce revealed that compensatory cis-trans eQTLs segreg

164 van-3-ols and PAs was investigated in Norway spruce saplings after wounding or inoculation with the f

165 pplying 54 g N/(15) N ha(-1) yr(-1) to Sitka spruce saplings.

166 ions for the period 2061-2090 were found for spruce seedling height (0.64), and for beech bud break a

167 to the 22 Gbp loblolly pine and 20 Gbp white spruce sequencing datasets.

168 re therefore suitable alternatives to Norway spruce; Silver fir more so at higher altitudes.

169 suggest that PEG may improve the quality of spruce somatic embryos by promoting normal differentiati

170 , an alkaloid isolated from various pine and spruce species, was then carried out to exploit this ste

171 encoding the rate-limiting enzymes in Norway spruce stilbene and flavonoid biosynthesis were actively

172 and more so for saplings than adults of red spruce, sugar maple, yellow birch, cordate birch, and st

173 tely affected the most rapidly growing white spruce, suggesting that, under recent climate warming, d

174 White spruces that are able to resist SBW attack were reported

175 ompounds in the defence mechanisms of Norway spruce to C. rhododendri.

176 nds and their role in enhanced resistance of spruce to infection by needle bladder rust are unknown.

177 climate and land use, and the return of red spruce to lower elevations where past logging originally

178 The uptake of PACs into blue spruce tree wood was measured, with wood-air partition c

179 and ring width in a population of 1694 white spruce trees (Picea glauca).

180 C responses to temperature reveal that black spruce trees are experiencing moisture stress on both no

181 in the ability of I. typographus to colonize spruce trees.

182 We tested our system on black and white spruce, two paleoclimatically significant taxa in the No

183 ponded similarly to the 1976 drought, Norway spruce was least resistant and resilient to the 2003 sum

184 In experiments with Norway spruce, we increased transformation efficiencies 1000-fo

185 Future risks for spruce were high across Switzerland.

186 ypes of wood logs, namely, beech, birch, and spruce, were chemically characterized using thermal deso

187 Cultivating these species instead of Norway spruce will contribute to maintaining a high level of pr