ライフサイエンスコーパス: salmon

1 tric tons (from 5 to 31.5 million individual salmon).

2 sed to distinguish fresh and thawed Atlantic salmon.

3 nsformation products (TPs) of EQ in Atlantic salmon.

4 s which each infect wild Chinook and sockeye salmon.

5 ess were found, as compared to the unwrapped salmon.

6 has decreased this stimulation in landlocked salmon.

7 n both strains but was greater in anadromous salmon.

8 paralogs (tshbetaa and tshbetab) in Atlantic salmon.

9 killer whales that feed primarily on Chinook salmon.

10 ere greater in anadromous than in landlocked salmon.

11 several salmonid genera, including Atlantic salmon.

12 le is known about viruses endemic to Pacific salmon.

13 ed strong associations to the flesh color in salmon.

14 functions that result from bears foraging on salmon.

15 yeasts, plants, crustaceans and fish such as salmon.

16 rom these the first clonal lines in Atlantic salmon.

17 anism for reduced fitness in hatchery-reared salmon.

18 itch to a large-scale production of triploid salmon.

19 validated using 15 processed food containing salmon.

20 breaking drought on endangered juvenile Coho salmon.

21 RNA in formalin-fixed tissues from the wild salmon.

22 pistasis in a quantitative trait in Atlantic salmon.

23 I 21-169); shrimp, 46 mg kg(-1) (UI 10-224); salmon, 27 mg kg(-1) (UI 17-41) and a pooled species gro

24 polysis decreased in marinated (46%) and raw salmon (57%) compared to the cooked matrix (67%).

25 quency of IgE-binding compared to those from salmon (77% vs 70% and 64% vs 53%, respectively).

26 We introduce Salmon, a lightweight method for quantifying transcript

27 Chinook salmon, a species of high cultural and economic value, h

28 s sealcoat runoff was more acutely lethal to salmon, a spectrum of cardiovascular abnormalities was c

29 most important in difficult times where the salmon abundance is low to moderate.

30 roportional contributions to each hearth and salmon abundance.

31 uring before 1990, the reduced size of adult salmon after 2010 has potentially resulted in substantia

32 ly) on pigment-depletion in vivo in Atlantic salmon after four weeks of challenge.

33 Four salmon allergens are well-characterized and registered w

34 stains the world's largest stocks of sockeye salmon along with four other salmon species.

35 Creatine kinase from salmon and catfish was detected by IgE from 14% and 10%

36 d fish allergy underwent skin prick tests to salmon and catfish.

37 ify, and compare all IgE-binding proteins in salmon and catfish.

38 al data indicate dogs predominantly consumed salmon and forage fish (35-65%), followed by nearshore f

39 This suggests that TPM values estimated from Salmon and Kallisto are the ideal RNA-seq measurements f

40 Salmon and Kallisto TPM data gives the best fit to the l

41 Predicting future impacts of drought on Coho salmon and other sensitive species will require identifi

42 50% of reduction compared to control), being salmon and sea bass proteolysis extent (40 and 33%, resp

43 ew will focus primarily on farmed salmonids (salmon and trout) within a comparative context and will

44 lized in three species (lake whitefish, coho salmon, and rainbow trout).

45 f magnitude, prevented mortality in juvenile salmon, and significantly reduced cardiotoxicity in zebr

46 One such orthomyxovirus, infectious salmon anemia virus (ISAV), spreads easily throughout fa

47 clude: limitation of preferred prey, Chinook salmon; anthropogenic noise and disturbance, which reduc

48 s the most important problem facing Atlantic Salmon aquaculture after feed sustainability.

49 causing severe economic losses for Atlantic salmon aquaculture.

50 mportant salmonid species.IMPORTANCE Chinook salmon are a keystone fish species of great ecological a

51 milarity in congener patterns indicated that salmon are a source of POPs to brook trout in stream rea

52 Seasonal patterns of life history in salmon are used to categorize them into ecotypes, which

53 s of exploited fish species, such as Pacific salmon, are vulnerable to a wide variety of anthropogeni

54 We exposed juvenile pink salmon as alevins to phenethyl alcohol (PEA) or control

55 the seminal fluid produced by a male Chinook salmon as he responds to increased reproductive competit

56 Finally, we demonstrate that the Atlantic salmon assembly can serve as a reference sequence for th

57 is work the trichloroacetic acid extracts of salmon backbones, heads and viscera stored at industrial

58 ributes to the continuing decline in Chinook salmon body size points to conflicting management and co

59 (sGnRH) and NR1 increased in the adult chum salmon brain during homing from the Bering Sea to the na

60 RT-qPCR demonstrated viral replication in salmon brains up to 15 days postinjection.

61 Hence, pink salmon bred in even years are completely reproductively

62 hales consume the largest biomass of Chinook salmon, but harbor seals (Phoca vitulina) consume the la

63 ated the genetic basis of growth in Atlantic salmon by exploiting the high level of genetic diversity

64 n layer formed during pH-shift processing of salmon by-products to pH-adjustment or freeze/thawing ef

65 bolites were detected and the possibility of salmon by-products utilization as a source of anserine,

66 d safe temperatures and times for storage of salmon by-products were proposed.

67 The potential of cross-processing herring or salmon by-products with brown seaweed, shrimp peeling by

68 ECD) in complex with a truncated analogue of salmon calcitonin ([BrPhe(22)]sCT(8-32)) has been determ

69 Furthermore, the amylin and GLP-1 analogs salmon calcitonin (sCT) and liraglutide produce synergis

70 All three proteins bound salmon calcitonin (sCT).

71 te GAG interactions with the peptide hormone salmon calcitonin (sCT).

72 tion of LDTg amylin receptors by the agonist salmon calcitonin dose-dependently reduces body weight,

73 thacrylate crosslinker, a small polypeptide (salmon calcitonin) loads and releases up to 45 mug/mg hy

74 s optimal performance for the small peptide, salmon calcitonin, whereas lower crosslinking density of

75 Here, we present two crystal structures of salmon calcitonin-bound, GlcNAc-bearing CTR ECD at 1.78

76 n captured upstream (wild-upstream) and wild-salmon captured downstream (wild-downstream).

77 least predator experience, followed by wild salmon captured upstream (wild-upstream) and wild-salmon

78 ecrotic microbial communities of decomposing salmon carcasses (Oncorhynchus keta) compared with those

79 lt migration characteristics of wild Chinook salmon caused by dam construction and other anthropogeni

80 Patagonian Chinook salmon clearly had a diverse and heterogeneous ancestry.

81 potential for production of further Atlantic salmon clonal lines, potentially with distinct character

82 Salmon combines a new dual-phase parallel inference algo

83 d that from 1975 to 2015, biomass of Chinook salmon consumed by pinnipeds and killer whales increased

84 and 13-16% of the spawning habitat for coho salmon could be lost by the 2040s and 2080s, respectivel

85 he life histories of some species of Pacific salmon could necessitate imprinting prior to the PST.

86 response to predator cues, whereas hatchery salmon did not change travel speed.

87 8 PCB and 6 PBDE congeners found in spawning salmon directly to those in resident stream fish.

88 aturity, traits long perceived as central to salmon ecotypes.

89 Atlantic salmon eggs fertilized with UV irradiated sperm combined

90 d heritable phenotypic plasticity in Pacific salmon embryos, we measured the developmental rate, surv

91 e expression and ultimate success of diverse salmon emigration behaviors in an anthropogenically alte

92 ses that are also widely distributed in wild salmon, emphasizes the potential role that viral disease

93 dict the evolutionary consequences of farmed salmon escapees interbreeding with wild conspecifics.

94 de pirimiphos-methyl (PM) in farmed Atlantic salmon exposed to contaminated feed was used as a case s

95 We found that pink salmon exposed to PEA as alevins were attracted to the c

96 ed fish allergy, with focus on cod, tuna and salmon extracts.

97 nt and environment surfaces in a cold-smoked salmon facility.

98 composition of over 3,000 Scottish Atlantic salmon farmed between 2006 and 2015, we find that terres

99 ion has been paid to this area in freshwater salmon farming.

100 would further increase the sustainability of salmon farming.

101 Ensuring lumpfish health and welfare in salmon farms is vital to reduce the high mortality rates

102 resistance in bacteria isolated from marine salmon farms, but much less attention has been paid to t

103 ance after 38 EMB treatments on six Atlantic salmon farms, in a small archipelago in British Colombia

104 status of lumpfish deployed in four Faroese salmon farms, several welfare indicators were assessed:

105 nal life cycle assessment is used to compare salmon feeds based on protein from soy, methanotrophic b

106 gest that incorporating SCP ingredients into salmon feeds can help reduce the environmental impacts o

107 as replacements for plant-based proteins in salmon feeds.

108 EQ was transferred from the feed to salmon fillets and 23 TPs were characterized, resulting

109 After the feeding trial, salmon fillets were extracted in acetonitrile and analyz

110 ower connective tissue stability of Atlantic salmon fillets.

111 orth America, and compare these estimates to salmon fisheries.

112 The proposed salmon flavivirus (SFV) has a 10.3-kb genome that encode

113 to use the formation of aspartate in stored salmon flesh as a marker of salmon freezing/thawing.

114 ch includes stocking with foreign and native salmon for at least 2 decades.

115 could alter stream habitats used by Pacific salmon for reproduction, with negative consequences for

116 downstream migration and pre-adapts juvenile salmon for seawater entry.

117 ound to establish dietary recommendations of salmon for specific population groups.

118 It was found that salmon freezing/thawing caused a significant increase in

119 artate in stored salmon flesh as a marker of salmon freezing/thawing.

120 harboured in the distal digesta of Atlantic salmon freshwater fish (FW) kept in a commercial Scottis

121 different life-history strategies of sockeye salmon from Bristol Bay, Alaska, over the past half-cent

122 ality rates (Z(M)) where higher for Atlantic salmon from Canada, Ireland, and Spain (Z(P) = 0.60-1.32

123 y qPCR throughout smoltification in Atlantic salmon from the endangered Loire-Allier population raise

124 Gene expression of salmon gonadotropin-releasing hormone (sGnRH) and NR1 in

125 he magnitude of reaction to predator cues by salmon group followed the gradient of previous predator

126 Both wild salmon groups slowed down in response to predator cues,

127 of S. salar in food ingredients based on the salmon growth hormone gene 1 (GH1).

128 esent the first in-depth characterization of salmon gut microbiota based on high-throughput sequencin

129 Salmon had the highest concentration followed by canned

130 Hatchery salmon had the least predator experience, followed by wi

131 The decrease in adult Chinook salmon harvest from 1975-2015 was 16,400 to 9,600 metric

132 competition from wild and hatchery-released salmon, have tended to delay maturation toward the salmo

133 , 2.6% and 8.0% for tilapia, catfish, trout, salmon, hybrid striped bass and yellow perch, respective

134 es (PP, positive correlation) encountered by salmon in common domains during their marine migration.

135 ur analyses identified the important role of salmon in contaminant biotransport but also demonstrated

136 Salmon in independent tanks were given feed containing e

137 nly suggest that many pools sustain juvenile salmon in non-drought years transition into ecological t

138 ve differently between domesticated and wild salmon in response to stress.

139 In rivers supporting Pacific salmon in southeast Alaska, USA, regional trends toward

140 erka) and Chinook (Oncorhynchus tshawytscha) salmon in the Northeast Pacific is of great concern.

141 mate warming has decreased the time spent by salmon in their natal freshwater habitat, as climate-enh

142 ectin benzoate (EMB) has been widely used by salmon industries around the world to control sea lice i

143 d have become the most widespread anadromous salmon invasion ever documented.

144 The Atlantic salmon is one of the best studied fish species globally,

145 Salmon is the main dietary source of omega-3 lipids and

146 Salmon kept at 10 degrees C grew the fastest.

147 cosa from mid and distal intestine of 67.3 g salmon kept in seawater (12-14 degrees C) and fed a comm

148 As a reference, diploid salmon kept under equal conditions and with equal geneti

149 Salmon lice parasitize the surface of the fish, feeding

150 Salmon lice, including the parasitic copepod Lepeophthei

151 Smoltification is a metamorphic event in salmon life history, which initiates downstream migratio

152 g selected (FP) and unselected (WP) Atlantic salmon lines that were reared together to avoid any envi

153 roduced the first documented cloned Atlantic salmon lines.

154 ory characteristics of milk, the immobilised salmon lipase has potential applications in developing d

155 other fish such as horse mackerel, sardine, salmon, mackerel, codfish, and tuna.

156 All pink salmon mature at age two and die after breeding.

157 Compared to salmon maturing before 1990, the reduced size of adult s

158 solation of a flavivirus from wild migrating salmon may indicate an emerging disease threat, characte

159 ences between wild and domesticated Atlantic salmon may provide insights into some of the genomic cha

160 ort but also demonstrated that the extent of salmon-mediated POP transfer and uptake in Great Lakes t

161 auses unexplained acute mortality when adult salmon migrate to urban creeks to reproduce.

162 ent reductions in summer flows when up-river salmon migrations occur.

163 llowing intracoelomic injection in a Chinook salmon model of infection.

164 We analyzed two decades of Chinook salmon monitoring data to explore the influence of regul

165 s hydrophila and Vibrio harveyi, to Atlantic salmon mucins isolated from different epithelial sites,

166 s tested on two data sets (human gastric and salmon mucosa O-linked glycomes) for which MS/MS spectra

167 quantification of triacylglycerols (TAGs) in salmon muscle tissue were conducted using electrospray i

168 2-22:6 (9.0%), and 18:0-18:1-22:6 (16.4%) in salmon muscle tissue.

169 tion of fumarate and phenylalanine in stored salmon muscle.

170 Chinook salmon native to North America are spreading through Sou

171 htly lower DNA packing densities compared to salmon nuclei despite salmon protamine lacking cysteine

172 Chinook salmon (O. tshawytscha) populations across Alaska have d

173 kisutch), rainbow trout (O. mykiss), Chinook salmon (O. tshawytscha), Atlantic salmon (Salmo salar),

174 The discovery in dead and dying farmed salmon of previously unrecognised viruses that are also

175 ycerides, free fatty acids and ergosterol in salmon oil.

176 r FO (n = 5 cows; fish oil manufactured from salmon oil; 2.9% of DM).

177 forming quantification of Aquadvantage(R) GM salmon on future genetically modified (GM) fish to be co

178 ses the effects of exposure on juvenile coho salmon ( Onchorhynchus kisutch).

179 ion and content of diploid and triploid pink salmon Oncorhynchus gorbuscha, reared in aquaculture in

180 of a behavioural assay with juvenile Chinook salmon Oncorhynchus tshawytscha that varied in their pas

181 ory; whereas the unique life history of pink salmon (Oncorhynchus gorbuscha) presents an opportunity

182 off from sealcoated asphalt on juvenile coho salmon (Oncorhynchus kisutch) and embryo-larval zebrafis

183 s a model, we studied immune-stimulated coho salmon (Oncorhynchus kisutch) from three experiment grou

184 ion at the DNA level in hatchery-reared coho salmon (Oncorhynchus kisutch) with those of their wild c

185 ake whitefish (Coregonus clupeaformis), coho salmon (Oncorhynchus kisutch), rainbow trout (O. mykiss)

186 In U.S. Pacific Northwest coho salmon (Oncorhynchus kisutch), stormwater exposure annua

187 tween its primary trophic resources, sockeye salmon (Oncorhynchus nerka) and red elderberry (Sambucus

188 ear (Ursus arctos) predation in wild sockeye salmon (Oncorhynchus nerka) populations spawning in pris

189 ze at hatching in two populations of sockeye salmon (Oncorhynchus nerka) that overlap in timing of sp

190 The ecosystems supporting Pacific salmon (Oncorhynchus spp.) are changing rapidly as a res

191 In the Great Lakes, introduced Pacific salmon (Oncorhynchus spp.) can transport persistent orga

192 ly and economically important group, Pacific salmon (Oncorhynchus spp.), experience site-specific the

193 We isolated a Chinook salmon (Oncorhynchus tshawytscha) cell line, GS2, with a

194 rus from fish was made from moribund Chinook salmon (Oncorhynchus tshawytscha) from the Eel River, Ca

195 and killer whales (Orcinus orca) on Chinook salmon (Oncorhynchus tshawytscha) has changed since the

196 of immobilised digestive lipase from Chinook salmon (Oncorhynchus tshawytscha) to generate flavour co

197 inct seasonal migration patterns) of Chinook salmon (Oncorhynchus tshawytscha), a phenotypically dive

198 s in an externally fertilising fish, chinook salmon (Oncorhynchus tshawytscha), and find that in less

199 the Lower Columbia River were introduced for salmon open-ocean ranching in the late 1970s and 1980s,

200 plication occurred in the kidneys of Chinook salmon or in tissues of rainbow trout (Oncorhynchus myki

201 The salmon PI, however, by itself had very low oxidation lev

202 ships using the embryonic stage of a Chinook salmon population.

203 age and size structure observed for Chinook salmon populations along the west coast of North America

204 ve success (RS) was estimated in two sockeye salmon populations for two consecutive brood years with

205 ived salmon scales to show that the original salmon populations from Lake Ontario completed their ent

206 indicators on the productivity of 15 Chinook salmon populations in the Cook Inlet basin, southcentral

207 Threats to salmon populations include habitat degradation, climate

208 over five decades in four marginal Atlantic salmon populations located at the southern limit of the

209 Understanding how-and how consistently-salmon populations respond to changes at regional and wa

210 ings support the hypothesis of a response of salmon populations to large climate-induced changes in t

211 ts, indicating recurrent use of the site for salmon processing during the terminal Pleistocene.

212 ka, the last largely pristine North American salmon-producing region.

213 can help reduce the environmental impacts of salmon production.

214 densities compared to salmon nuclei despite salmon protamine lacking cysteine residues.

215 oxy-trans2-hexenal (HHE) in both herring and salmon protein isolates (PI) while seaweed and shrimp by

216 epigenetic variation between hatchery-reared salmon provides evidence for parallel epigenetic modific

217 nd some TPs were also detected in commercial salmon randomly sampled from different Norwegian fish fa

218 The processes used to develop the specific salmon reference gene case study are intended to serve a

219 Thus, Chinook salmon removals (harvest + consumption) increased in the

220 llance of dead and moribund cultured Chinook salmon revealed a novel arenavirus, reovirus and nidovir

221 nservation efforts for maintaining resilient salmon runs in a warming world.

222 t 15,483 high-confidence SVs in 492 Atlantic salmon (Salmo salar L.) sampled from a broad phylogeogra

223 ffect the flesh quality of triploid Atlantic salmon (Salmo salar L., 1.6+/-0.3kg).

224 s study were to identify lncRNAs in Atlantic salmon (Salmo salar) and evaluate their transcriptomic r

225 -depletion in the fillets of farmed Atlantic salmon (Salmo salar) arises after periods of elevated wa

226 Actually, Atlantic salmon (Salmo salar) is the species most transformed to

227 decline in marine survival rates of Atlantic salmon (Salmo salar) over the last four decades.

228 at nutrient pulses from decomposing Atlantic salmon (Salmo salar) parents alter selection pressures o

229 Atlantic salmon (Salmo salar) populations have declined range-wid

230 an predation and mortality of adult Atlantic salmon (Salmo salar) released from 12 rivers flowing int

231 ), Chinook salmon (O. tshawytscha), Atlantic salmon (Salmo salar), and Arctic charr (Salvelinus alpin

232 a high-quality genome assembly for Atlantic salmon (Salmo salar), and show that large genomic reorga

233 s); rainbow trout (Onchorynchus mykiss); and salmon (Salmo salar), in order to guarantee the intra-sp

234 oncentration of NO(3)(-) was found in smoked salmon samples (median = 60 mug/g) while NO(2)(-) was no

235 f pacu, 57% of shad, 57% of trout and 50% of salmon samples.

236 um and vitamins A and D3 bioaccessibility in salmon, sardine, sea bass and hake.

237 ine, meat-free dinner, milk, pizza, poultry, salmon, sausage, shrimp, sliced ham, tilapia, and vegeta

238 logical bones and historical museum-archived salmon scales to show that the original salmon populatio

239 set to investigate the habitat use of female salmon sharks across their broad range in the eastern No

240 Salmon sharks displayed remarkable plasticity in habitat

241 However, salmon sharks generally reduced their use of deeper wate

242 Moreover, the vertical distribution of salmon sharks indicates they were able to exploit low di

243 Salmon sharks Lamna ditropis are highly migratory, upper

244 Salmon sharks utilized a broad thermal niche and exhibit

245 s of >6000 wild juvenile Chinook and sockeye salmon showed divergent distributions of viruses, implyi

246 The gut microbiota of Atlantic salmon showed similarities with that of mammals.

247 riability; while TPM value from Kallisto and Salmon shows high linearity in all analyses.

248 The century-old maize (Zea mays) salmon silks mutation has been linked to the absence of

249 fied two loci as being capable of conferring salmon silks phenotypes, salmon silks1 (sm1) and sm2 Ben

250 pable of conferring salmon silks phenotypes, salmon silks1 (sm1) and sm2 Benefitting from available s

251 We highlight widespread declines in Pacific salmon size based on 60 years of measurements from 12.5

252 Declines in salmon size, primarily resulting from shifting age struc

253 ted bull trout consumption and growth during salmon smolt outmigrations under two scenarios: 1) daily

254 Snake River subyearling Chinook salmon smolts implanted with the injectable transmitter

255 rature) that vary among the watersheds where salmon spawn and rear.

256 and became available during the period when salmon spawned in tributary streams.

257 s to brook trout in stream reaches receiving salmon spawners from Lake Michigan and Lake Huron but no

258 We hypothesized that stream fish exposed to salmon spawners would have congener patterns similar to

259 Salmon spawning during 2003-2007 produced 57% fewer recr

260 e quality and extent of coho, chum, and pink salmon spawning habitat in over 800 southeast Alaska wat

261 Bears departed salmon spawning streams, where they typically kill 25-75

262 es varied widely across watersheds and among salmon species.

263 ocks of sockeye salmon along with four other salmon species.

264 , have tended to delay maturation toward the salmon spending an additional year feeding in the ocean.

265 manner, we pre-equilibrated ETV6 with excess salmon sperm DNA, a heterogeneous polymer, before exposi

266 pproved drugs, ascorbic acid 6-palmitate and salmon sperm protamine, that effectively inhibited anthr

267 l Staging System (ISS) stage of 1, and Durie-Salmon stage of IIIA.

268 ifferences between the domesticated and wild salmon strains studied here, reflecting the different se

269 ulpin differed from those of brook trout and salmon, suggesting that brook trout and mottled sculpin

270 l divergence of tshbeta paralogs in Atlantic salmon supports a specific role of tshbetab in smoltific

271 In nearly half of the stream pools, salmon survival during drought was similar to mean survi

272 We estimated the variability of cumulative salmon survival using mark-recapture of nearly 20,000 ta

273 We timed salmon swimming downstream through a mesh enclosure in t

274 st RNA in the formulation was preferred over salmon testes DNA as it had no effect on PCR amplificati

275 how they stabilize the production of Pacific salmon that support valuable fisheries.

276 ultured catfish production surpassed that of salmon, the globally most-cultured marine species.

277 d have congener patterns similar to those of salmon, the presumed contaminant source.

278 In salmon, these proteins could not be separated successful

279 t brook trout and mottled sculpin either use salmon tissue to differing degrees, acquire POPs from di

280 the prioritization of screening in different salmon tissues (liver, kidney, bile, muscle, and fat) of

281 n combination with chitosan for wrapping raw salmon to produce a ready-to-eat product enriched in cal

282 bjecting raw, marinated and microwave-cooked salmon to static in vitro digestion under healthy (pH 7,

283 ams, where they typically kill 25-75% of the salmon, to forage on berries on adjacent hillsides.

284 s utilised for the recovery of proteins from salmon trimmings (ST), yielding 93% (w/w) protein.

285 focused on popular cold-water fishes (e.g., salmon, trout, and char) with relatively large body size

286 Atlantic salmon undergo dramatic physiological changes as they mi

287 ts of the models show substantial anadromous salmon use in multiple USR components, indicating recurr

288 found that POP congener patterns of Pacific salmon varied among regions in the Great Lakes basin (i.

289 losses to ecosystems and people; for Chinook salmon we estimated average per-fish reductions in egg p

290 the nature and extent of POP biotransport by salmon, we compared 58 PCB and 6 PBDE congeners found in

291 ncing and tribal fishery sampling of Chinook salmon, we show that a single, small genomic region is n

292 offspring of wild and domesticated Atlantic salmon were compared using a common-garden experiment un

293 r traits, anadromous and landlocked Atlantic salmon were reared under identical conditions and examin

294 eted study of polyunsaturated fatty acids in salmon where the protective outer skin was repetitively

295 rly applicable to migratory species, such as salmon, where distinct temporal changes in growth and ph

296 n both strains but were higher in anadromous salmon, whereas plasma thyroid hormones did not differ.

297 timated effects were lower for pink and chum salmon, which primarily spawn in unconfined floodplain s

298 l spawning habitat loss was highest for coho salmon, which spawn over a wide range of geomorphic sett

299 Long-term management strategies for Chinook salmon will need to consider potential conflicts between

300 xpression following WAF exposure on juvenile salmon with differential sensitivity between males and f