ライフサイエンスコーパス: oyster

1 olyticus illness from the consumption of raw oysters).

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

3 nterpreting the evolutionary genetics of the oyster.

4 f this family of histone demethylases in the oyster.

5 35.60 to 760.40 for Zn in the soft tissue of oysters.

6 ion of contaminated seafood, most infamously oysters.

7 the tissue concentrations of toxic metals in oysters.

8 matic and nacreous shell layers in the pearl oysters.

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

10 xin produced by strains isolated from market oysters.

11 s the high inorganic content is exclusive to oysters.

12 and efficient bacterial retention by feeding oysters.

13 resulted from ingestion of contaminated raw oysters.

14 diverse biological materials such as Pacific oysters.

15 served for microsatellite markers in Pacific oysters.

16 nts tested and from environmental samples of oysters.

17 tly involved in shell crystal production for oysters.

18 the consumption of raw seafood, particularly oysters.

19 ontaminates filter-feeding shellfish such as oysters.

20 had no influence on NoV contamination in the oysters.

21 hey were absent from tissues of unchallenged oysters.

22 m carbonate deposition in the shell of pearl oysters.

23 8%), pink hamburger (7% versus 4%), and raw oysters (2% versus 0.4%).

24 ithin 4 days of consuming raw or undercooked oysters, a stool specimen should be tested for Vibrio sp

25 le nonnegative equilibria can exist for live oyster, accreting reef and sediment volume at an ecologi

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

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

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

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

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

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

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

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

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

35 derived from a natural population of Pacific oysters and classical crossbreeding experiments, we comp

36 for pathogen prevention and detection in raw oysters and presents technological advances and impedime

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

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

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

40 ighly lethal sepsis after consumption of raw oysters and wound infection.

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

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

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

44 Oysters appear to use every possible mechanism to create

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

46 nd inbreeding depression and establishes the oyster as an animal model for understanding the genetic

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

48 All oysters associated with the outbreak were harvested when

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

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

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

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

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

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

55 Oyster beds met current bacteriologic standards during h

56 us outbreaks by closing potentially affected oyster beds.

57 Oyster bindin is a single-copy gene encoding a diversity

58 Oyster bindins have a conserved N-terminal region follow

59 Oyster "bioextraction" of nutrients and how oyster aquac

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

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

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

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

64 ns should understand that raw or undercooked oysters can cause illness even if harvested from monitor

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

66 is Gram-negative bacterium that contaminates oysters, causing highly lethal sepsis after consumption

67 With a description of oyster cement in hand we gain strategies for developing

68 que aspects are both revealed when comparing oyster cement to the adhesives of other marine organisms

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

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

71 y and contrast estuarine salinity, season of oyster collection, and shell provenance during Jamestown

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

73 Densities of oyster consumers were weakly influenced by predators at

74 s produces human disease associated with raw-oyster consumption or wound infections, but fatalities a

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

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

77 Sperm acrosomes of the Pacific oyster Crassostrea gigas contain the protein bindin that

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

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

80 ions was previously inferred for the Pacific oyster Crassostrea gigas, from massive distortions of zy

81 emale consensus linkage maps for the Pacific oyster Crassostrea gigas, using a total of 102 microsate

82 r Crassostrea virginica, but not the Pacific oyster Crassostrea gigas.

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

84 Oyster Crassostrea hongkongensis, a widely cultivated oy

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

86 marinus causes Dermo disease in the eastern oyster Crassostrea virginica and is responsible for cata

87 MB genomic sequence database from the cupped oyster Crassostrea virginica revealed the presence of a

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

89 nt of Dermo, a lethal disease of the eastern oyster Crassostrea virginica, but not the Pacific oyster

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

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

92 s underlying growth heterosis in the Pacific oyster (Crassostrea gigas) in two partially inbred (f =

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

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

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

96 Eastern oyster (Crassostrea virginica) reproduction season coinc

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

98 ing transcriptome-level responses of Pacific oysters (Crassostrea gigas) to various environmental str

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

100 Oysters (Crassostrea virginica) were a central component

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

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

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

104 lly reported metallothionein of the American oyster, Crassostrea virginica showed the canonical mollu

105 ture and domain organization in the American oyster, Crassostrea virginica.

106 tative intracellular parasite of the Eastern oyster, Crassostrea virginica.

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

108 The oysters cultivated in the winter presented some nutritio

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

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

111 Oyster density was fourfold greater on high-relief than

112 cruitment and reef accretion correlated with oyster density, facilitating reef development and popula

113 Exploitation for oysters did not occur randomly along continental margins

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

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

116 te gastroenteritis reported having eaten raw oysters during the week before their illness occurred.

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

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

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

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

121 lerant and two heat shock sensitive full-sib oyster families.

122 ratures in July and August at the implicated oyster farm increased 0.21 degrees C per year (P<0.001 b

123 Oyster fisheries expanded and collapsed in a linear sequ

124 re, I evaluate the expansion and collapse of oyster fisheries in 28 estuaries along three continental

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

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

127 r toward the colony, thereby enhancing local oyster food resources.

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

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

130 We compare oysters from archaeological sites with Pleistocene oyste

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

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

133 in second-generation autotetraploid Pacific oysters from gametic frequencies.

134 Stomach microbiomes in oysters from Hackberry Bay were overwhelmingly dominated

135 As each successive fishery collapsed, oysters from more distant estuaries were fished and tran

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

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

138 ers suggest that the colonists also obtained oysters from reefs near Chesapeake Bay to augment oyster

139 e incredible losses of large vertebrates and oysters from the entire Atlantic coast.

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

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

142 4 microatm; and 6.7, pCO2 18480 microatm) on oyster gametogenesis, fertilization, and early larval de

143 ly is associated with the consumption of raw oysters gathered from warm-water estuaries.

144 Experiments presented here show that oysters generate a biomineralized adhesive material for

145 Oyster glycogen-stimulated neutrophil transmigration int

146 ve Jamestown Island, facilitating individual oyster growth and extension of oyster habitat upriver to

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

148 ng individual oyster growth and extension of oyster habitat upriver toward the colony, thereby enhanc

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

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

151 reported having gastroenteritis after eating oysters harvested from Galveston Bay.

152 an opportunistic pathogen that contaminates oysters harvested from the Gulf of Mexico.

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

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

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

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

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

158 In this study, we show that oyster hemocytes recognize P. marinus via a novel galect

159 Inside oyster hemocytes, trophozoites resist oxidative killing,

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

161 creened showed over-expression in challenged oysters in both species, validating the SSH method.

162 ing in the 19th century reduced vast beds of oysters in Chesapeake Bay and other estuaries to a few p

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

164 fferences in gene expression between the two oysters in response to P. marinus infection, providing c

165 kely that, while filter feeding, the healthy oysters ingest P. marinus trophozoites released to the w

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

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

168 Oyster isolates were preferentially selected for the pre

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

170 distinguishing feature between clinical and oyster isolates.

171 esis were highly related across clinical and oyster isolates.

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

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

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

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

176 A second extensive subfamily of oyster metallothioneins (designated as CvMT-II) has appa

177 Oyster metallothioneins have been characterized as cDNA

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

179 Oyster monitoring sites were positioned at intervals dow

180 pulated to test predator identity effects on oyster mortality.

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

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

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

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

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

186 assign certified values for methylmercury in oyster, mussel, and fish tissue CRMs.

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

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 riving metapopulation comprising 185 million oysters of various age classes.

197 Liver, oyster, or mycobacterial glycogens were the best accepto

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

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

200 Oysters (Ostreidae), ecosystem engineers in many estuari

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

202 The facultative intracellular oyster parasite, Perkinsus marinus, taxonomically relate

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

204 estrial pathogens, including coral diseases, oyster pathogens, crop pathogens, Rift Valley fever, and

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

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

207 ein in the nacre layer of the Japanese pearl oysters (Pinctada fucata).

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

209 Native oyster populations in Chesapeake Bay have been the focus

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

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

212 After ingestion of contaminated oysters, predisposed people may experience highly lethal

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

214 h levels of sequence polymorphism in Pacific oysters, Q-PCR amplification is sub-optimal in some indi

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

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

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

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

219 he existence of alternative stable states in oyster reef populations.

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

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

222 ine ecology, yet the timing and magnitude of oyster-reef degradation in estuaries is poorly quantifie

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

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

225 Degradation of oyster reefs by destructive fishing practices in particu

226 e of parameter values; the initial height of oyster reefs determined which equilibrium was reached.

227 are) field experiment by constructing native oyster reefs of three types (high-relief, low-relief, an

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

229 Coastal ecosystems rely upon oyster reefs to filter water, provide protection from st

230 s derived from fishery records to infer when oyster reefs were degraded.

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

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

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

234 Between 1993 and 1996, three oyster-related gastroenteritis outbreaks attributed to N

235 to concentrate virus particles suggest that oyster-related outbreaks will continue unless strong con

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

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

238 OA during gametogenesis caused disruption in oyster reproduction.

239 and regulations regarding the safety of raw oysters require reevaluation.

240 rs from reefs near Chesapeake Bay to augment oyster resources near Jamestown Island.

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

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

243 method, an NLV G2 strain was identified in 2 oyster samples implicated in a 1998 California outbreak

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

245 The patient had consumed raw oysters several days before presentation.

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

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

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

249 ajor pharmaceutical companies not of natural oyster shell derivation.

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

251 The oyster shell season of harvest reconstructions suggest t

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

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

254 Although oyster shells were discarded as trash after the oysters

255 oxygen isotope data from these 17th century oyster shells with modern shells to quantify and contras

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

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

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

259 Native oyster species were once vital ecosystem engineers, but

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

261 d validates ecological restoration of native oyster species.

262 When Crassostrea gigas oyster sperm acrosome react a ring of bindin protein is

263 ism in organisms as diverse as trout, tunas, oysters, squid, turtles, locusts, hummingbirds, seals, a

264 ed by Planctomyctes occurred in Lake Caillou oyster stomachs.

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

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

267 000 km the northernmost documented source of oysters that caused illness due to V. parahaemolyticus.

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

269 cury in four marine tissue CRMs ranging from oyster tissue at 13.0 +/- 1.0 microg/kg to fish tissue a

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

271 mpounds and 4.6% for a 33-component mimic of oyster tissue.

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

273 virus particles in stool, and the ability of oysters to concentrate virus particles suggest that oyst

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

275 of genetic data from a population of Pacific oysters to infer the parameters of the model.

276 To understand the response of these two oysters to parasite exposure, a suppression subtractive

277 eactivity in the vestibular labyrinth of the oyster toadfish by using whole end organs labeled by imm

278 Oyster toadfish densities also did not change with incre

279 The experimental model was the oyster toadfish, Opsanus tau.

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

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

282 s; the attack rate among people who consumed oysters was 29 percent.

283 stic-regression analysis, consumption of raw oysters was the only significant predictor of illness; t

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

285 ral capsid nucleotide sequences derived from oysters were 100% identical to those derived from a pati

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

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

288 Data show that oysters were collected during an extended drought betwee

289 ter shells were discarded as trash after the oysters were eaten, the environmental and ecological dat

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

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

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

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

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

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

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

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

300 metapopulation is the largest of any native oyster worldwide and validates ecological restoration of