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1 iomass accumulation in a perennial temperate grass.
2 ccasionally isolated from trees, shrubs, and grass.
3 riginated very early in the evolution of the grasses.
4 levated Si concentrations compared with C(3) grasses.
5 ae) versus branch-formation in non-Triticeae grasses.
6 ctive approach for dwarfing breeding of turf grasses.
7 ators of cell wall polymers deposition in C4 grasses.
8 y, particularly for inflorescences of cereal grasses.
9 raits potentially related to g(m) in 18 C(4) grasses.
10 escence meristematic boundaries of different grasses.
11 der optimal and water stress environments in grasses.
12 functional genomics of temperate cereals and grasses.
13 rstand traits of importance to Andropogoneae grasses.
14 lopment are limited to Arabidopsis and a few grasses.
15 an inverse correlation with g(sw) among C(4) grasses.
16 is usually poor except for spring trees and grasses.
17 r and greater composition of invasive annual grasses.
18 into pathways controlling AMs development in grasses.
19 validations and root growth improvements in grasses.
20 lants and crops to kill broadleaf plants and grasses.
21 d in functional genomics studies of other C3 grasses.
22 s little influence on the ratio of C(3):C(4) grasses.
23 ps, including rice and wheat, and in various grasses.
24 emperate C(3) grasses and (sub)tropical C(4) grasses.
25 Paspalum vaginatum) is a halophytic Panicoid grass able to grow in salt concentrations near that of s
26 of p-hydroxycinnamyl alcohols (monolignols), grasses additionally use a flavone, tricin, as a natural
29 ity of ACC measurement) were significant for grass AIT (P < 0.001) but not significant for birch AIT
30 the efficacy/safety of 4 dosing regimens of grass allergen peptides after a second (GPS2) and third
33 , placebo-controlled study demonstrated that grass allergen peptides significantly improved total rhi
34 th microarray data, IgE to the major timothy grass allergen Phleum pratense 1 (Phl p 1) and the cat a
37 ) by -13.55 (-17.56, -9.54; P < 0.001) after grass and -9.81 (-14.13, -5.50; P < 0.001) after birch A
38 Chloris truncata, an Australian native C(4) grass and a summer-fallow weed, which is common in no-ti
39 were no significant annual fluctuations, but grass and Ambrosia pollen counts are increasing in some
41 nitions to properly mirror symptom loads for grass and birch pollen-induced allergic rhinitis in othe
42 have shown negligible effects of dust-laden grass and browse, suggesting that intrinsic properties o
43 bryophytes and higher land plants of monocot grass and dicot lineages and identified positively selec
44 initions on pollen season for both birch and grass and for a variety of geographical locations for th
46 igher shrub and bare ground cover, and lower grass and herbaceous species cover relative to adjacent
52 ation of seeds from graminoid plants such as grasses and sedges could have formed a critical element
53 oid defense metabolites that are produced by grasses and sequestered by a specialist maize herbivore,
54 urther understanding lignin deposition in C4 grasses and will ultimately allow the validation of biot
55 Differences between the life histories of grasses and woody species led to a contrasting prevalenc
56 te change may influence silica deposition in grasses and, by extension, alter the important ecologica
57 different natural forages: lucerne, timothy grass, and bamboo with distinct phytolith/silica content
59 phylogenetic pattern of flowering control in grasses, and how this relates to broad- and fine-scale n
61 iridis), a model species for studies of C(4) grasses, and use the resource to probe domestication gen
66 er several years leads to increased standing grass biomass and fuel loads, and, therefore, in larger
71 by the roots of maize (Zea maize), palisade grass (Brachiaria brizantha cv. Marandu) and ruzigrass (
72 ecosystem (EcoFAB) devices to grow the model grass Brachypodium distachyon in three distinct media ac
73 In this work putative orthologs in the model grass Brachypodium distachyon were tested for their abil
74 We conducted a study on the model perennial grass Brachypodium sylvaticum to investigate the molecul
76 ots pine than in endomycorrhizal reed canary grass, but nonetheless, both species showed soil-derived
77 PL8 induce phase transition and flowering in grasses by directly upregulating SEPALLATA3 (SEP3) and M
79 al grasses, compared with C(3) and perennial grasses, came from the faster growth of individual modul
82 bined experimental work demonstrates that in grass caryopses the coleorhiza indeed controls germinati
87 diversity-dependent changes in biomass of C3 grass colonists, which decreased under low diversity and
89 backs in grasslands, facilitation in a beach grass community, and niche differences with independent
90 ish whether faster growth in C(4) and annual grasses, compared with C(3) and perennial grasses, came
93 hanged seasonality is driving the changes in grass cover, whereas fire has little influence on the ra
97 d C(4) photosynthetic pathways, whereas C(3) grasses decline after the mid-Pleistocene transition (MP
98 tion and soil characteristics (e.g., crop or grass designation, minimum annual LAI, soil coarse fragm
100 ave greater ecological value than unaffected grass dominated sites, particularly given the recent dec
104 ath-like organ that surrounds the radicle in grass embryos, performs the same role in the grass weed
106 mic approaches with the desiccation-tolerant grass Eragrostis nindensis and the related desiccation-s
107 f the Poaceae TPS-a subfamily arose early in grass evolution and the reactions catalyzed have become
108 re, we test the classic hypothesis that C(4) grasses evolved stronger mechanical defenses than C(3) g
110 n of the TPS-a subfamily in the Poaceae (the grass family), a plant family that contains important cr
112 rences in wear patterns, with those of fresh grass feeders being similar to fresh and dry lucerne (ph
117 modification of lignocellulosic biomass from grasses for improved biofuel and biochemical production
119 ckets form, diversity is reduced with little grass/forb cover, while transpiration and annual product
120 ed by the movement of grazers, which reduced grass fuel and fires, weakened the capacity of soils to
122 Using reported measurements, we developed grass functional trait values (physiological, structural
123 mplex has been promoted as a plant model for grass genomics with translation to small grain and bioma
126 ers, supporting previous reports that "fresh grass grazers" show less abrasion than unspecialized gra
129 ing the study period, the estimated onset of grass growth advanced on average by 0.54 days/year in ea
130 ies Brachypodium distachyon as well as other grasses has revealed numerous features of the grass cell
131 Since their origin in the early Cretaceous, grasses have diversified across every continent on Earth
135 heir growth strategies and root systems, the grass Holcus lanatus and the forb Rumex acetosa, to 2 wk
138 asticity among 12 populations of an invasive grass (Imperata cylindrica), and to determine whether th
139 ulative field experiment with an annual C(4) grass in a forest understory to differentially track its
140 ) after posttreatment challenge (PTC) to rye grass in an environmental exposure unit after 1 interven
142 and inoculant on the productivity of forage grasses in Brazil (Brachiaria spp. and Panicum spp.) was
144 w these findings may inform virus studies of grasses in the laboratory, field and natural settings.
145 ent evolution of herbaceous lineages such as grasses in young habitat types may drive coexistence of
147 et most Land Surface Models (LSMs) summarise grasses into two generic PFTs based primarily on differe
148 fire regimes, coupled with the importance of grass invasion in modeling these differences, suggest th
149 rrence, size, and frequency as a function of grass invasion, in addition to anthropogenic and ecologi
150 rmination by coleorhiza-enforced dormancy in grasses is an example of the convergent evolution of mec
152 er in (a) tropical vs temperate regions; (b) grass/legume mixtures vs grass monocultures; and (c) soi
153 Awns, bristle-like structures extending from grass lemmas, provide protection against predators, cont
156 ertilisation and lime treatments of the Park Grass long term experiment at Rothamsted Research, UK.
158 : miscanthus > poplar > switchgrass > native grasses ~ maize stover (residue) > restored prairie ~ ea
159 enetic manipulation of CAldOMTs conserved in grasses may serve as a potent strategy to improve bioref
162 typic and biomass properties between the two grass model systems highlight the challenges and opportu
163 perate regions; (b) grass/legume mixtures vs grass monocultures; and (c) soil pH of 5-6 vs other pHs.
165 ally important browsers of coastal saltmarsh grasses of eastern North America and the Caribbean.
166 at ~2.7 Ma indicating the expansion of C(4) grasses on the landscape was concurrent with the first a
167 re, CD4(+) T cells from donors sensitized to grass or birch pollen were stimulated with autologous al
168 influenced vegetation composition, favouring grasses over Calluna vulgaris, and led to a reduction in
170 ifferent types of perennial crops (perennial grasses, palms, and woody plants) with different end use
171 mentation (Co): FoCo fed high-quality Napier grass (Pennisetum purpureum), FeCo supplemented maize si
172 g mechanisms of salt tolerance in halophytic grasses, plants that thrive in salt conditions, may be a
179 this study was to evaluate the usefulness of grass pollen allergen molecules for prediction of grass
180 oded antibodies that were specific for major grass pollen allergens and able to elicit basophil activ
182 (R)35 cells were quantified in patients with grass pollen allergy (seasonal allergic rhinitis [SAR] g
183 (SLIT) intervention improves the control of grass pollen allergy by maintaining allergen tolerance a
184 pollen allergen molecules for prediction of grass pollen allergy during childhood and up to adolesce
187 ing from allergic rhinoconjunctivitis due to grass pollen allergy were randomized to receive subcutan
188 omogenates were collected from patients with grass pollen allergy with CRSwNP and nonallergic control
191 nvestigate the correlation between birch and grass pollen concentrations during the birch and grass p
193 , tricolor granulocyte activation test using grass pollen demonstrated MRGPRX2 upregulation associate
195 stigated the associations between short-term grass pollen exposure and lung function and airway infla
198 her in NHS ester-coated slides after timothy grass pollen extract stimulation appearing a suitable su
203 ; however, sensitization to birch as well as grass pollen Phl p 1 and cat Fel d 1 allergen molecules
206 s pollen concentrations during the birch and grass pollen season defined via the EAACI criteria, and
211 ollicular regulatory (T(FR)) cells following grass pollen subcutaneous immunotherapy (SCIT) and subli
214 mmunotherapy (SLIT) for allergy to temperate grass pollen, predominantly to ryegrass pollen (RGP; Lol
215 cT(FH) cells were initially evaluated in the grass pollen-allergic (GPA) group (n = 28) and nonatopic
223 lent Biome, an assemblage of succulent-rich, grass-poor, seasonally dry tropical vegetation distribut
224 stover >> miscanthus ~ switchgrass ~ native grasses ~ poplar > early successional >= restored prairi
226 Additionally, we assessed whether invasive grass presence is a significant predictor of altered fir
228 yrosine hydroxylase in the brain of the Nile Grass rat (NGR), a novel and potentially significant fin
230 significantly as the replacement of forbs by grasses resulted in changes in relative abundance across
231 by funder mandates, institutional policies, grass-roots advocacy, and changing attitudes in the rese
234 gest a prominent role for agriculture in the grass's western spread, although glacial history and env
238 dary, repeated measures of IgE and IgG(4) to grass showed significant between-group difference and wi
241 ic clines among continents of the intertidal grass Spartina alterniflora within its invasive and nati
243 ere acquired recently from distantly related grass species [5, 11, 16], to test the hypothesis that t
245 ween fire regimes experienced by hundreds of grass species and their persistence strategy, within a p
246 uvate carboxylase (Ppc) gene from three C(4) grass species could drive M-cell-specific expression of
249 is tillering effect was transferable between grass species, and overexpression of LNJ in barley and r
250 phylogenetic comparative experiment with 74 grass species, conceptualising morphogenesis as the bran
251 both consume grasses, and feedbacks between grass species, their functional traits, and consumers ha
258 ugs (Leptoglossus phyllopus, Hemiptera), (2) grass stinkbugs (Mormidea pama, Hemiptera), (3) Asian la
259 This review focuses on genetic regulation of grass stomatal development and prospects for the future,
261 he evolution of life-cycle strategies in the grass subfamily Pooideae and test if transitions between
262 r density of fine roots produced by palisade grass, subtly decreased nitrate leaching potential throu
265 about 19% of the S. italica TPSs in related grasses supports a common ancestry of selected pathway b
267 wth depends on ecological context, with C(4) grasses tending to promote resource capture under compet
268 c landscape of 35S rDNA in an allotetraploid grass that exhibits ND, Brachypodium hybridum (genome co
269 sitivity varies between different species of grass that flower at different times, but it is not know
271 wever, the genetic elements that distinguish grasses that are sensitive versus tolerant to extreme dr
272 emmas of wheat (Triticum aestivum) and other grasses that contribute to photosynthesis and play a rol
273 y represents a novel regulatory mechanism in grasses that is largely different from that in Arabidops
274 ceae constitute a taxon of flowering plants (grasses) that cover almost all Earth's inhabitable range
275 olved stronger mechanical defenses than C(3) grasses through increased phytolith deposition, in respo
277 stead, we propose that the tendency for C(4) grasses to outcompete C(3) species under hot, dry condit
278 avoidance mechanism of cool season perennial grasses to persist well under harsh summer conditions.
279 l functioning across three vegetation zones: grass, transitional, and shrub in a coastal grassland.
280 m (Sorghum bicolor) and its relatives in the grass tribe Andropogoneae bear their flowers in pairs of
284 t the MPT, lead to the local decline of C(3) grasses under conditions of decreased water availability
285 Brachypodium distachyon is an annual C3 grass used as a monocot model system in functional genom
286 is produces fast growth in different ways in grasses using C(4) and C(3) photosynthesis, and in annua
287 ruct pseudomolecules for allotetraploid lawn grass utilizing PacBio long reads in combination with re
288 A world collection of sugarcane and related grasses (WCSRG) maintained at Miami, FL contains > 1,200
289 into the evolution of C(4) photosynthesis in grasses, we examined leaf gas exchange, anatomy and ultr
291 red from sympatric potato, mint, mustard and grasses were characterized genotypically with microsatel
292 mmunities with higher biomass of resident C4 grasses were more resistant to colonization by legume, n
293 nscription factor function, we turned to the grasses, where interactions between B-class MADS box pro
295 is particularly troublesome when evaluating grasses, whose members represent our most agriculturally
297 oss- and gain-of-function mutations in black-grass with genotype specificity and measurable changes i
299 tional capacity varied, with C. fulviceps (a grass-wood-feeder) gut microbiome samples containing mor
300 ription factor binding in leaves of the C(4) grasses Zea mays, Sorghum bicolor, and Setaria italica a