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1 s of transspecies evolution within the genus Oncorhynchus.
2 of trans-species evolution within the genus Oncorhynchus.
4 to observations of Coastal Cutthroat Trout (Oncorhynchus clarkii clarkii) occurrence and variables r
5 Q exposure on coastal cutthroat trout (CCT) (Oncorhynchus clarkii clarkii), a species sympatric with
6 in median length of Coastal Cutthroat Trout Oncorhynchus clarkii clarkii, but a coexisting species,
8 hus tshawytscha), westslope cutthroat trout (Oncorhynchus clarkii lewisi), and nonfry life stages of
9 Native Colorado River cutthroat trout (CRCT; Oncorhynchus clarkii pleuriticus) are now relegated to 3
13 reas the unique life history of pink salmon (Oncorhynchus gorbuscha) presents an opportunity to do so
14 content of diploid and triploid pink salmon Oncorhynchus gorbuscha, reared in aquaculture in a bay o
15 ncient DNA analyses establish the species as Oncorhynchus keta (chum salmon), and stable isotope anal
16 communities of decomposing salmon carcasses (Oncorhynchus keta) compared with those of terrestrial ne
17 the distributional responses of chum salmon (Oncorhynchus keta), a keystone species, to the recent cl
18 y-reared underyearling juvenile chum salmon (Oncorhynchus keta), thyrotropin-releasing hormone gene e
19 sealcoated asphalt on juvenile coho salmon (Oncorhynchus kisutch) and embryo-larval zebrafish (Danio
21 e-scale population structure of coho salmon (Oncorhynchus kisutch) by comparing archived (1938) and m
22 of concern owing to its role in coho salmon (Oncorhynchus kisutch) deaths via urban runoff mortality
23 the upper thermal tolerance of coho salmon (Oncorhynchus kisutch) during sustained swimming and acut
24 hwest, acute mortality of adult coho salmon (Oncorhynchus kisutch) follows rain events and is correla
25 l, we studied immune-stimulated coho salmon (Oncorhynchus kisutch) from three experiment groups shari
27 sh representing nine cohorts of coho salmon (Oncorhynchus kisutch) in California, we show that bimoda
28 anchors of biological decline: coho salmon (Oncorhynchus kisutch) mortality risk (p < 0.001) and los
29 gy, and habitat models within a coho salmon (Oncorhynchus kisutch) population model to assess how pro
30 or below 1 part per billion), juvenile coho (Oncorhynchus kisutch) were exposed to a range of mixture
31 he DNA level in hatchery-reared coho salmon (Oncorhynchus kisutch) with those of their wild counterpa
32 lop and apply this framework to coho salmon (Oncorhynchus kisutch), a highly migratory and culturally
33 s between such growth traits in coho salmon (Oncorhynchus kisutch), an important fish species distrib
34 in sensitive species, including coho salmon (Oncorhynchus kisutch), brook trout (Salvelinus fontinali
35 efish (Coregonus clupeaformis), coho salmon (Oncorhynchus kisutch), rainbow trout (O. mykiss), Chinoo
37 none) causes acute mortality in coho salmon (Oncorhynchus kisutch), yet its mechanisms of toxicity re
41 ial infections of a natural vertebrate host, Oncorhynchus mykiss (rainbow trout), with variants of a
42 erated recombinant C5a of the rainbow trout, Oncorhynchus mykiss (tC5a), and used fluoresceinated tC5
43 er subgroups (IFN-e and -f) in rainbow trout Oncorhynchus mykiss and analyzed the expression of all s
44 genes were identified in rainbow trout (rt) Oncorhynchus mykiss and are classified into two groups b
46 tracting sulfated polysaccharides (SPs) from Oncorhynchus mykiss byproducts using alkaline/acid solub
48 thermal tolerance of two populations of wild Oncorhynchus mykiss near the species' southern range lim
50 f widely introduced salmonids rainbow trout (Oncorhynchus mykiss) and brook trout (Salvelinus fontina
53 -anchored genome assembly for rainbow trout (Oncorhynchus mykiss) and characterize a 55-Mb double-inv
54 ed in two previous studies of rainbow trout (Oncorhynchus mykiss) and common carp (Cyprinus carpio).
55 hemicals in two fish species: rainbow trout (Oncorhynchus mykiss) and fathead minnow (Pimephales prom
56 out-migration success in juvenile steelhead (Oncorhynchus mykiss) and focuses on the application of m
57 o bioassays using rainbow trout hepatocytes (Oncorhynchus mykiss) and in vivo studies with Japanese m
58 isulfide polymerization of IgM in the trout (Oncorhynchus mykiss) and its effect on its half-life wer
59 luding two sensitive species, rainbow trout (Oncorhynchus mykiss) and lake trout (Salvelinus namaycus
60 lamin-binding proteins of the rainbow trout (Oncorhynchus mykiss) and to compare their properties wit
61 angliosides found in sperm of rainbow trout (Oncorhynchus mykiss) and was shown to be present promine
64 ntic salmon (Salmo salar) and rainbow trout (Oncorhynchus mykiss) are two of the most susceptible sal
66 ocal anadromous (ocean-run) steelhead trout (Oncorhynchus mykiss) by blocking their migration route a
69 unctional characterization of rainbow trout (Oncorhynchus mykiss) CD4-1(+) T cells and the establishm
70 hether a relevant model fish (rainbow trout, Oncorhynchus mykiss) could detect OSPW using its olfacto
71 r vitelline envelope (VE), of rainbow trout (Oncorhynchus mykiss) eggs consists of three proteins, ca
72 members within the available rainbow trout (Oncorhynchus mykiss) EST gene index, we identified a uni
73 o examine stress responses in rainbow trout (Oncorhynchus mykiss) exposed to five distinct environmen
75 the rancidity development in rainbow trout (Oncorhynchus mykiss) fillets during refrigerated storage
76 scle and edible skin parts of rainbow trout (Oncorhynchus mykiss) fillets, sampled at two growth stag
77 bile samples was validated in rainbow trout (Oncorhynchus mykiss) following short-term laboratory exp
78 mentation on a wild population of steelhead (Oncorhynchus mykiss) from the Hood River, Oregon, by mat
82 expression was studied in the rainbow trout (Oncorhynchus mykiss) gonad (RTG) (fibroblast) cell line.
83 vacuum packaged low processed rainbow trout (Oncorhynchus mykiss) gravad during storage at 7 +/- 1 de
84 vacuum packaged low processed rainbow trout (Oncorhynchus mykiss) gravad during storage at 7 1 C for
86 ry and sequence analysis of a rainbow trout (Oncorhynchus mykiss) IL-17A/F2 molecule and an IL-17RA r
87 th of the young of the year steelhead trout (Oncorhynchus mykiss) in the recipient tributary over the
88 al barrier model built on the rainbow trout (Oncorhynchus mykiss) intestinal cell line, RTgutGC and t
89 RTgutGC cells, derived from rainbow trout (Oncorhynchus mykiss) intestine, were used to evaluate th
90 this study, PFAS exposure on rainbow trout (Oncorhynchus mykiss) is examined at the molecular level,
93 n of plasmablasts and plasma cells in trout (Oncorhynchus mykiss) peripheral blood and splenic and an
94 d first-generation hatchery steelhead trout (Oncorhynchus mykiss) reared in a common environment.
95 not benzocaine or MS-222; and rainbow trout (Oncorhynchus mykiss) showed no avoidance to the three ag
96 ss<30kDa (PF30) isolated from rainbow trout (Oncorhynchus mykiss) skin gelatin hydrolysates was encap
97 ark dose (BMD) assay for rainbow trout (RBT; Oncorhynchus mykiss) to derive transcriptomic points-of-
98 nerve of a teleost fish, the rainbow trout (Oncorhynchus mykiss) to determine what types of somatose
99 ranscriptomics on the CNSS of rainbow trout (Oncorhynchus mykiss) to establish: (1) how the CNSS resp
100 ur studies have revealed that rainbow trout (Oncorhynchus mykiss) use a novel strategy for the genera
101 ith early life stages of rainbow trout (RBT; Oncorhynchus mykiss) using benzo[a]pyrene (B[a]P) as the
105 aquatic ecosystems, juvenile rainbow trout (Oncorhynchus mykiss) were separately exposed to a mixtur
106 ress this, adult and juvenile Rainbow Trout (Oncorhynchus mykiss) were, respectively, exposed for 96
107 her blastomeres isolated from rainbow trout (Oncorhynchus mykiss) will incorporate and continue to de
110 BPA deposition in the eggs of rainbow trout (Oncorhynchus mykiss), an ecologically and economically i
111 tlantic salmon (Salmo salar), rainbow trout (Oncorhynchus mykiss), and Arctic char (Salvelinus alpinu
112 tion mixtures in coho salmon, rainbow trout (Oncorhynchus mykiss), and fathead minnow (Pimephales pro
113 hic invertebrates, juvenile steelhead trout (Oncorhynchus mykiss), and water striders (Gerris remigis
114 vely affects muscle growth in rainbow trout (Oncorhynchus mykiss), but the mechanisms directing with
115 eta2m of a salmonid fish, the rainbow trout (Oncorhynchus mykiss), does not conform to the mammalian
116 of salmonid fishes, including rainbow trout (Oncorhynchus mykiss), experienced a whole genome duplica
117 ss (Dicentrarchus labrax) and rainbow trout (Oncorhynchus mykiss), fed diets at 25%, 50% and 60% inse
118 her vertebrate taxa including rainbow trout (Oncorhynchus mykiss), frog (Xenopus laevis), chicken (Ga
119 ly life stages of ammonotelic rainbow trout (Oncorhynchus mykiss), suggesting that the urea cycle may
120 (Salvelinus fontinalis), and rainbow trout (Oncorhynchus mykiss), suggesting that tolerant species m
122 n (Acipenser fulvescens), and rainbow trout (Oncorhynchus mykiss), were selected to evaluate TFM redu
123 ed to the controversy is that rainbow trout (Oncorhynchus mykiss), which have served as the primary m
140 mologue has been identified in rainbow trout Oncorhynchus mykiss, and its biological activities have
143 sory receptors on the head of rainbow trout, Oncorhynchus mykiss, using extracellular recording from
151 of iconic, keystone populations of sockeye (Oncorhynchus nerka) and Chinook (Oncorhynchus tshawytsch
152 s primary trophic resources, sockeye salmon (Oncorhynchus nerka) and red elderberry (Sambucus racemos
153 roductive behaviour of adult sockeye salmon (Oncorhynchus nerka) and the activity of their principal
154 e series from nine stocks of sockeye salmon (Oncorhynchus nerka) from the Fraser River system in Brit
155 ream-spawning populations of sockeye salmon (Oncorhynchus nerka) had similar reproductive success to
156 beach and creek ecotypes of sockeye salmon (Oncorhynchus nerka) in Little Togiak Lake, Alaska, to ex
157 us arctos) predation in wild sockeye salmon (Oncorhynchus nerka) populations spawning in pristine hab
158 was extremely high [during a sockeye salmon (Oncorhynchus nerka) smolt outmigration and at a counting
159 tching in two populations of sockeye salmon (Oncorhynchus nerka) that overlap in timing of spawning b
164 The ecosystems supporting Pacific salmon (Oncorhynchus spp.) are changing rapidly as a result of c
165 n the passage of juvenile Pacific salmonids (Oncorhynchus spp.) at seven dams in the Columbia/Snake R
167 the Great Lakes, introduced Pacific salmon (Oncorhynchus spp.) can transport persistent organic poll
169 conomically important group, Pacific salmon (Oncorhynchus spp.), experience site-specific thermal reg
170 tion or abundance for populations of salmon (Oncorhynchus spp.), groundfish, herring (Clupea pallasii
177 seasonal changes in juvenile Chinook Salmon Oncorhynchus tshawytscha size, growth and production ove
179 havioural assay with juvenile Chinook salmon Oncorhynchus tshawytscha that varied in their past preda
180 ar (YOY) growth potential of Chinook salmon (Oncorhynchus tshawytscha) and Dolly Varden (Salvelinus m
181 on the early life growth of Chinook salmon (Oncorhynchus tshawytscha) and steelhead (O. mykiss) in w
182 ol of locomotor activity in juvenile salmon (Oncorhynchus tshawytscha) by manipulating 3 neurotransmi
183 on and knockout studies in a Chinook salmon (Oncorhynchus tshawytscha) cell line were conducted to as
186 fish was made from moribund Chinook salmon (Oncorhynchus tshawytscha) from the Eel River, California
188 ler whales (Orcinus orca) on Chinook salmon (Oncorhynchus tshawytscha) has changed since the 1970s al
189 shing on the survival of the Chinook salmon (Oncorhynchus tshawytscha) in the Sandy River (OR, USA),
190 t age and age at maturity in Chinook salmon (Oncorhynchus tshawytscha) populations introduced to New
191 ly demonstrate that juvenile Chinook salmon (Oncorhynchus tshawytscha) respond to magnetic fields lik
192 of sockeye (Oncorhynchus nerka) and Chinook (Oncorhynchus tshawytscha) salmon in the Northeast Pacifi
193 I ask whether fluctuation in Chinook salmon (Oncorhynchus tshawytscha) spawner population size throug
194 ilised digestive lipase from Chinook salmon (Oncorhynchus tshawytscha) to generate flavour compounds
195 ally distinct populations of Chinook salmon (Oncorhynchus tshawytscha) within a single metapopulation
196 %, Snake River spring/summer chinook salmon (Oncorhynchus tshawytscha) would probably continue to dec
197 sonal migration patterns) of Chinook salmon (Oncorhynchus tshawytscha), a phenotypically diverse anad
198 externally fertilising fish, chinook salmon (Oncorhynchus tshawytscha), and find that in less than 48
200 n (Acipenser transmontanus), chinook salmon (Oncorhynchus tshawytscha), westslope cutthroat trout (On