ライフサイエンスコーパス: oyster

1 f this family of histone demethylases in the oyster.

2 arget of the parasite, and the plasma of the oyster.

3 ovide new insights into breeding research in oyster.

4 corporated to facilitate extensive uptake by oysters.

5 ion of contaminated seafood, most infamously oysters.

6 and efficient bacterial retention by feeding oysters.

7 had no influence on NoV contamination in the oysters.

8 hey were absent from tissues of unchallenged oysters.

9 m carbonate deposition in the shell of pearl oysters.

10 to promote high-level uptake of bacteria by oysters.

11 35.60 to 760.40 for Zn in the soft tissue of oysters.

12 the tissue concentrations of toxic metals in oysters.

13 matic and nacreous shell layers in the pearl oysters.

14 te (for Zn) was enhanced in the contaminated oysters.

15 xin produced by strains isolated from market oysters.

16 viously identified in Minnesota, both due to oysters.

17 ore pathogenic V. vulnificus than off-bottom oysters.

18 tomatically colonizes seafood, most commonly oysters.

19 ions from seafood is Vibrio, especially from oysters.

20 ction using the Molluscan Broodstock Program oysters.

21 resistance has yet to be evaluated in these oysters.

22 8%), pink hamburger (7% versus 4%), and raw oysters (2% versus 0.4%).

23 Stable isotope ratios in oyster adductor muscle were similar to shell for delta(1

24 (micro-PS) on the physiology of the Pacific oyster, adult oysters were experimentally exposed to vir

25 of Cd and Cu in the natural Zn-contaminated oysters also covaried with tissue Zn concentration, and

26 trations of the metals in the soft tissue of oyster and global guidelines clearly indicates that near

27 The molecular weights (MW) of glycogen from Oyster and mannan from Saccharomyces cerevisiae are dete

28 h, rice, soybean, pea, chlorella, spirulina, oyster and mussel.

29 ickel metal ion in the real samples of crab, oyster and rice by the designed magnetic nano adsorbent

30 In the case of dried oyster and shiitake mushrooms there was a decrease to th

31 e iridescent material of the shells of pearl oysters and abalone, consists mostly of aragonite (a for

32 nservative; removal by clams in Connecticut, oysters and clams in New York, and denitrification are n

33 oysters are considerably different from wild oysters and could possibly pose different health risks.

34 ytos mackini causes Denman Island disease of oysters and represents one of the most genetically diver

35 potential effects of light sensitive ENPs in oysters and their broader ecological impacts on estuarin

36 the time-course of metal bioaccumulation in oysters and was further validated by predicting the bioa

37 American fisheries were focused on nearshore oysters and were likely harvested at a rate that was sus

38 ions of Vibrio spp. in suspended, farm-grown oysters and wild oysters at three sites, using a paired

39 Vibrio bacteria are concentrated by oysters and, when consumed, infections can result with s

40 us, an intracellular parasite of the eastern oyster, and through yeast complementation, we demonstrat

41 wo main styles of tool use: axe hammering of oysters, and pound hammering of unattached encased foods

42 Japan to North America, as a hitch-hiker on oysters, and then intentional introduction in Europe, bu

43 We quantified oyster aquaculture GHG-emissions from the three main con

44 HG-release in terrestrial livestock systems, oyster aquaculture has less than 0.5% of the GHG-cost of

45 invader could threaten the sustainability of oyster aquaculture in Washington, which currently produc

46 eri Hartman have resulted in the collapse of oyster aquaculture industries in Australia, New Zealand,

47 Globally, oyster aquaculture is increasing as a way to meet growin

48 Oyster "bioextraction" of nutrients and how oyster aquaculture might complement existing management

49 and CH(4) were unchanged in the presence of oyster aquaculture, regardless of the length of time it

50 Farmed, or aquaculture raised, oysters are considerably different from wild oysters and

51 Farmed oysters are handled, raised from seed, and often grown u

52 Oysters are unusual among bivalves in that they possess

53 The decay rates of NoV in oysters as a function of the distance from the outfall w

54 emolyticus (sequence type 36 [ST36]) causing oyster-associated human illness.

55 Optimistically, the calculation of oyster-associated removal from all leases in both states

56 nce techniques, to identify X-ray irradiated oysters at five different dose levels in the range 0.1-2

57 p. in suspended, farm-grown oysters and wild oysters at three sites, using a paired approach with far

58 for such behavior in populations of Pacific oysters, based on estimates of their family sizes.

59 ed C and N and, therefore, no evidence of an oyster-based conduit to higher trophic levels.

60 ive to gage height (the depth of water in an oyster bed) and water temperature, followed by wind, rai

61 us outbreaks by closing potentially affected oyster beds.

62 ck oyster Saccostrea glomerata in a study of oysters being farmed in estuaries at aquaculture leases

63 Oyster "bioextraction" of nutrients and how oyster aquac

64 Broodstock Program, a US West Coast Pacific oyster breeding program, were screened for survival afte

65 long tributaries of the Chesapeake Bay where oyster breeding programs are concentrated.

66 ysters has been conducted on wild and farmed oysters but not at the same time.

67 nidaria (Hydra, sea anemones), and Mollusca (oysters) but not in most other animal phyla.

68 n of oil materials from the DWHOS to diet of oysters by comparing carbon (C) and nitrogen (N) stable

69 presence of nine Jumonji orthologues in the oyster C. gigas.

70 haracterized nine Jumonji orthologues in the oyster, called Cg-Jmj, bearing conserved domains critica

71 Therefore, farmed oysters can be grown at the surface of the estuary, whil

72 Eating raw oysters can come with serious health risks, as oysters c

73 Oysters can increase their tissue selenium level up to 5

74 sters can come with serious health risks, as oysters can potentially contain bacteria of the Vibrio g

75 l on the London Underground network based on Oyster card data, and (iii) the global airport network.

76 results showed that metal biokinetics in the oysters changed dramatically after suffering from metal

77 ferent samples evaluated (mussels, scallops, oysters, clams, cockles) nor interference from other she

78 strains were deficient relative to NT in an oyster colonization model, demonstrating a positive corr

79 d greater biofilm formation, aggregation and oyster colonization than its parent.

80 Densities of oyster consumers were weakly influenced by predators at

81 Invertebrates (shrimp, oyster, crab) and other nearshore species comprised the

82 ems, in particular marine calcifiers such as oysters, crabs, and corals.

83 ed Cu isotope variations of two bivalves-the oyster Crassostrea gigas and the mussel Mytilus edulis-o

84 We found here that the hemocytes of the oyster Crassostrea gigas release antimicrobial H1-like a

85 Despite the Pacific oyster Crassostrea gigas representing one of the most im

86 hell colors full-sib families of the Pacific oyster Crassostrea gigas, we systematically identified m

87 ull-length TIR-STING fusion from the Pacific oyster Crassostrea gigas.

88 the toxicokinetics of multiple metals in the oyster Crassostrea hongkongensis in a dynamic estuary po

89 Oyster Crassostrea hongkongensis, a widely cultivated oy

90 ion of Cd and Cu in three populations of the oyster Crassostrea hongkongensis.

91 uccess of an intertidal species, the eastern oyster Crassostrea virginica was evaluated in two-replic

92 We identified two AOX mRNAs in eastern oyster Crassostrea virginica, CvAOXA and CvAOXB, which d

93 Detailed annotation of the Pacific oyster (Crassostrea gigas) genome, a protostome inverteb

94 We exposed Pacific oyster (Crassostrea gigas) larvae (3-24 d.p.f.) to polys

95 The eastern oyster (Crassostrea virginica) has become a useful model

96 rica's Chesapeake Bay, once-thriving eastern oyster (Crassostrea virginica) populations have declined

97 Eastern oyster (Crassostrea virginica) reproduction season coinc

98 The galectin CvGal1 from the eastern oyster (Crassostrea virginica), which possesses four tan

99 ngs of mud blisters on the shells of Pacific oysters (Crassostrea gigas Thunberg) in Washington State

100 f seasonality on the chemical composition of oysters (Crassostrea rhizophorae).

101 Specimens were also obtained from eastern oysters (Crassostrea virginica Gmelin) collected in New

102 poxia and tributyltin (TBT) on adult Eastern oysters (Crassostrea virginica) exposed either in the la

103 harged, hepatopancreas and gill tissues from oysters (Crassostrea virginica) were exposed to concentr

104 ter the Deepwater Horizon Oil Spill (DWHOS), oysters (Crassostrea virginica) were exposed to oil and

105 he ontogenetic transcriptomes of the Pacific oyster, Crassostrea gigas (Bivalvia, Mollusca), the Paci

106 Here we propose the oyster, Crassostrea gigas, as a model for studying the i

107 To test this premise, eastern oysters, Crassostrea virginica, and blue mussels, Mytilu

108 esearchers to investigate the composition of oysters cultivated in different climates all over the wo

109 The oysters cultivated in the winter presented some nutritio

110 ial equations that represent volumes of live oysters, dead oyster shells (=accreting reef), and sedim

111 nant staghorn coral Acropora cervicornis and oyster Dendrostrea frons that lives attached to gorgonia

112 ealed novel microbial communities within the oyster digestive system, the functions of the oyster mic

113 currence of terminal blood group moieties on oyster dominin and on hemocyte surfaces can account in p

114 s were not exposed to oil; rather they imply oysters either did not consume oil-derived materials or

115 s and show that environmental calcium, which oysters enrich for shell repair and growth, regulates ia

116 ort a scenario in which the calcium-enriched oyster environment triggers IamP-mediated processing of

117 Finally, oyster ET formation was highly dependent on the producti

118 Importantly, oyster ETs were evidenced in vivo in hemocyte-infiltrate

119 ore levels regardless of the pCO2 level that oysters experienced as larvae.

120 We also report a novel finding: oysters exposed to atrazine concentrations as low as 3 u

121 We show that oyster families selectively bred for fast growth and fam

122 Oyster farming represents one of the most developed aqua

123 presentation of the environmental impact of oyster farming, existing and promising applications are

124 change; provide context for managing modern oyster fisheries in the Chesapeake Bay and elsewhere aro

125 loadings of NoV and E. coli in a commercial oyster fishery impacted by a WwTW.

126 There is no GHG-release from oyster fodder production.

127 lue sprat, burrowing blackfish, gummy shark, oyster (four species), ocean trout and yellowtail kingfi

128 increased substantially in the transplanted oysters from a reference site to a contaminated site.

129 We compare oysters from archaeological sites with Pleistocene oyste

130 Gut communities for oysters from both sites differed from stomach communitie

131 ibrio vulnificus was quantified in water and oysters from Florida's Gulf Coast by plating on mCPC aga

132 Stomach microbiomes in oysters from Hackberry Bay were overwhelmingly dominated

133 Levels of E. coli in oysters from more tidally influenced areas of the estuar

134 A total number of 50 oysters from North Sea, including 10 control samples, we

135 two emerging diseases of juvenile crabs and oysters from the UK using massively parallel sequencing

136 causing these blisters, we obtained Pacific oysters from two locations in Puget Sound and examined t

137 ite interactions due to the hijacking of the oyster galectin CvGal1 for host entry by the protozoan p

138 4 microatm; and 6.7, pCO2 18480 microatm) on oyster gametogenesis, fertilization, and early larval de

139 irus 1 (OsHV-1) cause high losses of Pacific oysters globally, including in Tomales Bay, California,

140 high mortalities of Pacific oysters in major oyster-growing regions outside of the United States.

141 ebsteri are present in the mud blisters from oysters grown in Puget Sound, constituting the first con

142 e of negative synergistic effects on Olympia oyster growth; rather, we found only additive and opposi

143 Interestingly, on-bottom oysters had more pathogenic V. vulnificus than off-botto

144 After 2 mo, exposed oysters had significant decreases in oocyte number (-38%

145 ern oyster reefs, and other records of human oyster harvest from around the world.

146 udied the fate of these microorganisms in an oyster harvesting area impacted by frequent stormwater d

147 virus outbreak data collected from Louisiana oyster harvesting areas along the Gulf of Mexico coast,

148 Previous research in North Carolina oysters has been conducted on wild and farmed oysters bu

149 development of specific-pathogen-free (SPF) oysters has enabled assessment of the infection process

150 nteractions and host genetics in determining oyster health and disease.

151 A parallel glycomic study carried out on oyster hemocytes determined the structures of oligosacch

152 In field-deployed oysters, HIF1-alpha and Tbeta-4 expression increased, wh

153 all raw mushroom preparations, but only raw Oyster (IC(5)(0)=0.035 mg/ml), Shiitake (IC(5)(0)=0.047

154 irulent strains were cytotoxic to hemocytes, oyster immune cells.

155 ars), cause very high mortalities of Pacific oysters in major oyster-growing regions outside of the U

156 played an important role in the survival of oysters in metal contaminated environment.

157 There are currently no known Pacific oysters in the United States that are resistant to OsHV-

158 ortantly, we show that selective breeding in oysters is likely to be an important global mitigation s

159 vivo study of bacterial interactions within oysters is limited by the inability to promote high-leve

160 e observed for clinical isolates, and 7 (9%) oyster isolates belonged to serotype O1:KUT.

161 The two oyster isolates containing tdh but not trh possessed all

162 Oyster isolates were preferentially selected for the pre

163 ypes, 9 of which were shared by clinical and oyster isolates.

164 distinguishing feature between clinical and oyster isolates.

165 Phylogenic analyses revealed that oyster Jumonji cluster into two distinct groups: 'single

166 itu and in toto hybridizations indicate that oyster Jumonji genes are transcribed mostly within the g

167 en model growth rate and duration of Olympia oyster larvae and predict the suitability of habitats fo

168 lish Sea are actually suboptimal for Olympia oyster larvae from populations in the region, and that l

169 o- and nanoplastics were readily ingested by oyster larvae, exposure to plastic concentrations exceed

170 We focused on molluscs, and chose Pacific oyster Magallana gigas as experimental model.

171 Specimens of the Pacific oyster Magallana gigas, an oyster well known for chalk e

172 acterization of miRNAs profiles expressed in oyster mantle, which might facilitate understanding the

173 demonstrates that contamination of metals in oysters may result from concurrent exposure to other met

174 king, release mud and detritus that can foul oyster meats.

175 yster digestive system, the functions of the oyster microbiome are largely unknown.

176 Oyster monitoring sites were positioned at intervals dow

177 pulated to test predator identity effects on oyster mortality.

178 us edodes), Enoki (Flammulina velutipes) and Oyster mushroom (Pleurotus ostreatus) preparations were

179 One serving of UV-B pretreated sliced oyster mushroom covered the weekly demand of vitamin D o

180 The basidiomycete oyster mushroom Pleurotus ostreatus is a carnivorous fun

181 Fruiting bodies of the oyster mushroom Pleurotus ostreatus were illuminated wit

182 rming MACPF protein, pleurotolysin (from the oyster mushroom), also favors the delivery of cationic m

183 Pleurotus florida, an edible species of oyster mushrooms, was grown on wheat straw from the sele

184 products from the European southwest coast (oysters, mussels, salmon organs, glass eels).

185 t form was named, MgNACR, as it grouped with oyster nacreins (NACR).

186 A enzyme in mantle and that by homology with oyster nacreins likely regulates mussel shell production

187 Cultivated hard clam and eastern oyster nitrogen removal in Greenwich Bay, Connecticut, w

188 Modeling and prediction of oyster norovirus outbreaks along Gulf of Mexico coast.

189 The ability to predict oyster norovirus outbreaks at their onset may make it po

190 The NORF model predicted all historical oyster norovirus outbreaks from 1994 through 2014.

191 further confirmation, but they suggest that oyster norovirus outbreaks may be predictable using the

192 Oyster norovirus outbreaks often pose high risks to huma

193 a mathematical model for predicting risks of oyster norovirus outbreaks using environmental predictor

194 obiomes of Crassostrea virginica, the Easter oyster, obtained from two sites, one in Barataria Bay (H

195 cs: mussels, scallops and snails but none in oyster, octopus and squid.

196 We reared Olympia oyster (Ostrea lurida) larvae in laboratory cultures und

197 tact sediment cores containing European flat oysters (Ostrea edulis) or blue mussels (Mytilus edulis)

198 Oysters (Ostreidae), ecosystem engineers in many estuari

199 game meat (P < 0.01), offal (P < 0.001), and oysters (P = 0.02).

200 uses substantial mortality in inbred Pacific oysters, particularly during metamorphosis, a critical d

201 ragonite formation in the shell of the pearl oyster Pinctada fucata.

202 In the Japanese pearl oyster (Pinctada fucata), this process is mediated by a

203 hrooms including shiitake (Lentinus edodes), oyster (Pleurotus ostreatus), tea tree (Agrocybe aegerit

204 Native oyster populations in Chesapeake Bay have been the focus

205 effects on ecosystems including the loss of oyster populations in Galveston Bay.

206 Slow recovery of depleted eastern oyster populations in the Chesapeake Bay, USA has prompt

207 These data document resilience in oyster populations under long-term Native American harve

208 work for alternative stable states in native oyster populations, and can be used as a tool to improve

209 portion of five different seafood organisms: oysters, prawns, squid, crabs, and sardines.

210 Oysters preferentially ingested the 6-microm micro-PS ov

211 s a relationship between chalk formation and oyster processes of cementation.

212 cascade was linked to regional gradients in oyster recruitment to and sediment accumulation on reefs

213 benefits of suppressed consumer foraging on oyster recruits exceeded costs of sediment accumulation

214 We manipulated oyster reef communities to test the generality of potent

215 We found that oyster reef growth is unimodal relative to emergence, wi

216 the DWH accident using data obtained from an oyster reef restoration project in coastal Alabama.

217 erally failed to rebuild the populations and oyster reef structure.

218 we show the effects of emergence on vertical oyster-reef growth by determining the conditions at whic

219 ach to characterize patterns of diversity on oyster reefs across a range of geographic scales compris

220 Oyster reefs are vital to estuarine health, but they exp

221 s from archaeological sites with Pleistocene oyster reefs that existed before human harvest, modern o

222 hin intertidal areas, constructed or natural oyster reefs will persist and function best as green inf

223 low-energy environments where salt marshes, oyster reefs, and mangroves can develop and survive exte

224 fs that existed before human harvest, modern oyster reefs, and other records of human oyster harvest

225 ches and dunes, seagrass beds, and coral and oyster reefs.

226 velopment and 12 x greater omega-3 levels in oysters relative to conventional live algal diets.

227 We found that oysters release no methane (CH(4)) and only negligible a

228 However, Eastern oyster reproduction was resilient to moderate OA project

229 could represent a significant bottleneck for oyster reproduction which may have profound negative imp

230 OA during gametogenesis caused disruption in oyster reproduction.

231 ed and wild-type families of the Sydney rock oyster Saccostrea glomerata in a study of oysters being

232 Finally, oysters sampled from a restored reef displayed comparabl

233 using a paired approach with farmed and wild oysters sampled in proximity.

234 termination of synthetic polycyclic musks in oyster samples by using one-step microwave-assisted head

235 tion difference between PAHs detected in the oyster samples for the current study and the 10-year his

236 the determination of trace level of AHTN in oyster samples was also demonstrated.

237 lian counterparts, the two SECIS elements in oyster SelenoP (3'UTR recoding elements) do not show fun

238 We show that oyster SelenoP mRNA with 46 UGAs is translated full-leng

239 )(4).65H(2)O that consists of a unique "open oyster" shaped structure (U(19)) with intramolecular H-b

240 s were also tested over 60 days, longer than oyster shelf life confirming the applicability and feasi

241 Average delta(13)C and delta(15)N values in oyster shell (-21 +/- 1 per thousand and 9-11 per thousa

242 ral oyster shell (NOS), the calcined natural oyster shell (CNOS), and biomolecules of the organic mat

243 set of the OS was heated to produce calcined oyster shell (COS).

244 ed from the oyster shell, namely the natural oyster shell (NOS), the calcined natural oyster shell (C

245 oric acid to produce phosphoric-acid-treated oyster shell (POS).

246 onstitutes the first critical compilation on oyster shell applications, with the aim to provide essen

247 than the 19th century and support the use of oyster shell delta(15)N values as a useful environmental

248 shellfish there as indicated by huge ancient oyster shell middens on all continents.

249 ground to <=100 um particle size to produce oyster shell powder (OS).

250 C) and nitrogen (N) stable isotope ratios in oyster shell to ratios in suspended particulate matter (

251 37 residential spaces enclosed by ridges of oyster shell up to 4 m tall.

252 acid (1.6 mM and 3.2 mM) to produce OS + P (oyster shell with phosphoric acid) and COS + P (calcined

253 with phosphoric acid) and COS + P (calcined oyster shell with phosphoric acid).

254 o the type of raw materials derived from the oyster shell, namely the natural oyster shell (NOS), the

255 les of the organic matrix extracted from the oyster shell.

256 that represent volumes of live oysters, dead oyster shells (=accreting reef), and sediment.

257 These results indicate that oyster shells can be an effective sorbent for fluoride r

258 Discarded oyster shells were ground to <=100 um particle size to p

259 Three-dimensional reconstructions of oyster shells were used to assess the overall distributi

260 to better comprehend the recycling of waste oyster shells.

261 Here we present data on oyster size and human harvest from Chesapeake Bay archae

262 g the extraction efficiency of analytes from oyster slurry were systematically investigated and optim

263 assostrea hongkongensis, a widely cultivated oyster species in Southern China, can accumulate metals

264 s natural and artificial repopulation of the oyster species within the Bay.

265 a virginica) and brooding (Ostrea equestris) oyster species.

266 ed by Planctomyctes occurred in Lake Caillou oyster stomachs.

267 After 8 days of exposure to hypoxia + TBT, oysters substantially up-regulated HIF1-alpha and down-r

268 iciency were significantly higher in exposed oysters, suggesting compensatory and physical effects on

269 er amplitudes in the isotope variations than oysters, suggesting that each species incorporates Cu is

270 ich offsets heavy sedimentation and promotes oyster survival, disease resistance and growth, in contr

271 ificant shift in the microbiomes of juvenile oysters that reduces fitness and impedes natural and art

272 United States was replaced with protein from oysters, the GHG savings would be equivalent to 10.8 mil

273 th so many people consuming contaminated raw oysters, the incidence of severe V. vulnificus disease i

274 d using the certified reference materials of oyster tissue (NIST 1566b) and mussel tissue (NIST 2977)

275 ugh analysis of standard reference material, Oyster Tissue (NIST 1566b) and Tea (NCS DC 73351).

276 tion of nickel metal ion in the crab tissue, oyster tissue and rice samples were performed and the ob

277 extraction conditions were achieved when the oyster tissue mixed with 10-mL deionised water (containi

278 crobial histones were found to accumulate in oyster tissues following injury or infection with vibrio

279 the physiological process of acclimation in oysters to illustrate how they cope with increasing meta

280 cies in an ecologically relevant host model, oyster, to study interactions with marine Vibrio species

281 Oyster toadfish densities also did not change with incre

282 wn at the surface of the estuary, while wild oysters typically grow at the bottom of the water column

283 with foodborne illness: pink hamburger, raw oysters, unpasteurized milk, cheese made from unpasteuri

284 In this study, 77 clinical and 67 oyster Vibrio parahaemolyticus isolates from North Ameri

285 ring the experiment, metal concentrations in oysters, water, and suspended particles were intensively

286 ns of the Pacific oyster Magallana gigas, an oyster well known for chalk expression, were grown in Bo

287 Beside the change of metal homeostasis, the oysters were able to sequester metals into subcellular n

288 g of 86 fishes, 65 shrimps, 59 crabs, and 68 oysters were collected and analyzed weekly from May 27,

289 the physiology of the Pacific oyster, adult oysters were experimentally exposed to virgin micro-PS (

290 In the laboratory, oysters were exposed to either hypoxia followed by a rec

291 These findings are not an indication that oysters were not exposed to oil; rather they imply oyste

292 transcribed mostly within the gonad in adult oysters whereas they display a ubiquitous expression dur

293 ne system, preventing systemic infections in oysters, whereas the successful infection of virulent st

294 h, and elevated maintenance costs in exposed oysters, which is thought to be caused by interference w

295 The primary features of the oyster whole hemocyte N-glycome were also found in domin

296 ting that the potential stressor exposure to oysters will drastically differ over moderate spatial sc

297 implies that efforts to conserve and restore oysters will require an adaptive approach that incorpora

298 ets showed higher gene flow for the brooding oyster with more oceanic salinity tolerances.

299 A comparison of microbiomes from Louisiana oysters with bacterial communities reported for other ma

300 concentrations and the Cu-hyperaccumulating oysters with variable concentrations that track Cu bioav

301 modifications and reproductive disruption in oysters, with significant impacts on offspring.