ライフサイエンスコーパス: mussel

1 and the filter-feeding behavior of the blue mussel.

2 inactivation of E. coli after uptake by the mussel.

3 ion exhibited by adhesion proteins of marine mussel.

4 ybean, pea, chlorella, spirulina, oyster and mussel.

5 ecies, Mytilus californianus, the California mussel.

6 ological function and toxin-pathogen load in mussels.

7 bility but was unaffected by the presence of mussels.

8 reduced nutrient concentrations and invasive mussels.

9 al Ti background, which varied in individual mussels.

10 reissena bugensis) and zebra (D. polymorpha) mussels.

11 erred the evolution of effective adhesion by mussels.

12 e prevalence and genotype(s) of T. gondii in mussels.

13 nal content properties between the different mussels.

14 ting marine habitat contamination using wild mussels.

15 d problems in discrimination these in cooked mussels.

16 we estimate chemical depuration kinetics for mussels.

17 ius subsp. coli isolates from sea otters and mussels.

18 reported within are the first for freshwater mussels.

19 ell as the genuine material produced by live mussels.

20 imilar to the novel foot proteins from other mussels.

21 d to that of biological adhesion, e.g., from mussels.

22 so in O. cf. ovata extracts and contaminated mussels.

23 stage of the colonization of invasive quagga mussels.

24 -)(1)), shrimp (0.075-0.374 mug g(-)(1)) and mussel (0.206-0.397 mug g(-)(1)).

25 Thirteen mussels (1.4%) had detectable T. gondii DNA and the pres

26 s (2 GPa) resemble those observed in related mussels, a more effective dispersion of microdamage enab

27 when subjected to feeding pressure by quagga mussels, a widespread aquatic invasive species.

28 pecies richness was positively correlated to mussel abundance in mid to high intertidal zones.

29 that can govern the dynamic distribution of mussel abundance over 1,800 km of coastline.

30 longest mussel chronologies (1982-2003; PC1(mussel)) accounted for 47% of the dataset variability an

31 Surveys and mussel addition experiments indicate this positive effec

32 is recognized as a key chemical signature of mussel adhesion and has been adopted into diverse synthe

33 This study expands the scope of translating mussel adhesion from simple Dopa-functionalization to mi

34 f macromolecules to mimic complex aspects of mussel adhesion still constitutes a challenge.

35 umerous attempts have been made to translate mussel adhesion to diverse synthetic platforms.

36 t challenges to the practical translation of mussel adhesion.

37 of a carbon nanotube (CNT) fiber inspired by mussel-adhesion chemistry is described.

38 ol-metal ion coordination chemistry found in mussel adhesive proteins is developed.

39 2002/657/UE guidelines, and applied it to 50 mussel and 50 clam samples derived from various Food and

40 cross-linked proteins provides an analogy to mussel and barnacle adhesives whereas the high inorganic

41 (tuna and plaice) but decreased in molluscs (mussel and octopus).

42 The three immunoassays performed well with mussel and scallop matrixes displaying adequate dynamic

43 e that thermal buffering by centimetre-thick mussel and seaweed beds eliminates differences in stress

44 e molecular tools for T. gondii detection in mussels and (ii) apply optimized methods in a surveillan

45 (see phylogenetic tree; Figure 1); Bivalvia (mussels and clams), protected by shells and practically

46 Filter feeders, like mussels and clams, are suitable bioindicators of environ

47 ol for monitoring VOC profiles of Greenshell mussels and could aid in the development of technologies

48 eractions in the form of a mutualism between mussels and dominant cordgrass in salt marshes enhance e

49 tential to be a complementary tool to survey mussels and enhance current efforts to monitor and prote

50 ignificant toxicological consequences to the mussels and higher trophic consumers.

51 onfirm the identity of this compound in blue mussels and investigate whether the analyte is diOH- and

52 ccurs in self-assembled holdfast proteins in mussels and other marine organisms, is generally thought

53 shed a symbiosis with Bathymodiolus heckerae mussels and poecilosclerid sponges from asphalt-rich, de

54 lorinated biphenyls (PCBs) concentrations in mussels and sediments.

55 ples from aquaculture facilities, wild grown mussels and waste material.

56 PC1(mussel) and PC1(discharge) were closely linked to region

57 bitats for over 60% of North America's fish, mussel, and crayfish species.

58 lychaete worms (Siboglinidae), bathymodiolid mussels, and alvinocaridid shrimps, are absent from the

59 a good proxy to assess Vtg levels in marine mussels, and careful verification of the adequacy of the

60 s and crustose algae, they were overgrown by mussels, and the subsequent detachment of the mussels re

61 xamines the ability of the native freshwater mussel Anodonta californiensis and an invasive freshwate

62 o species of freshwater bivalves, the native mussel Anodonta californiensis and the invasive clam Cor

63 Removal of E. coli by the native freshwater mussel Anodonta californiensis was studied using laborat

64 For instance, marine mussels are able to attach to a broad spectrum of hard s

65 indicating that early life stages of mytilid mussels are largely tolerant to a broad range of [O2 ] r

66 Mussels are opportunistic macrofouling organisms that ca

67 Mussels are subjected to severe mechanical impacts cause

68 Freshwater mussels are vital components of stream ecosystems, yet r

69 The Mytilidae, generally known as marine mussels, are known to attach to most substrates includin

70 urthermore, the importance of monitoring the mussel as food material in respect to contaminations wit

71 The consumption of marine mussels as popular seafood has increased steadily over t

72 or the interpretation of metabolomic data in mussels, as well as the impact of environmental stress i

73 spatial scales: regularly spaced clusters of mussels at centimeter scale driven by behavioral aggrega

74 levels that are rather variable among female mussels at different stages of gonad development.

75 how the network of byssus threads keeps the mussel attached in this challenging mechanical environme

76 fused coatings exhibit very low preferential mussel attachment and ultralow adhesive strengths under

77 Deep-sea mussels (Bathymodiolinae) are globally distributed at de

78 somallon squamiferum and Gigantopelta aegis, mussel Bathymodiolus marisindicus, and Neolepas sp. stal

79 connectivity of ecologically important vent mussels (Bathymodiolus spp.) from the Mid-Atlantic Ridge

80 ry, and much higher levels needed to control mussel bed development.

81 e two spatial scales of self-organization on mussel bed persistence, we conducted field manipulations

82 attern formation improves the persistence of mussel beds (Mytilus edulis) on intertidal flats.

83 Results demonstrate that mussel beds both increase and decrease thermal stresses.

84 edulis) during spatial pattern formation in mussel beds can be regarded as being the first three lev

85 enhanced the persistence of the constructed mussel beds in comparison to nonorganized beds.

86 Using experiments with self-organizing mussel beds, we derive an empirical relation between the

87 ed as having little environmental impact yet mussel biodeposits and shell debris accumulate around th

88 nt efforts to monitor and protect freshwater mussel biodiversity.

89 smission widespread in gonochoric freshwater mussels (Bivalvia: Palaeoheterodonta: Unionida).

90 ty level, on the crab functional response to mussel (Brachidontes exustus) prey.

91 ess and high extensibility of the cuticle of mussel byssal threads and proposed to endow self-healing

92 age, sponge spicules) to attachment devices (mussel byssal threads), from both invertebrate and verte

93 Inspired by cuticles of marine mussel byssi, we circumvent this inherent trade-off by i

94 Our findings demonstrated that the zebra mussel byssus cDNA microarray is an efficient tool for t

95 perienced by proteins during maturation of a mussel byssus secretion, we have developed a simple meth

96 aterials covering a broad range of matrices: mussels, cabbage, seaweed (hijiki), fish protein, rice,

97 ding principal component of the five longest mussel chronologies (1982-2003; PC1(mussel)) accounted f

98 ystems and imparted a coherent pattern among mussel chronologies.

99 alidated and then applied on 959 wild-caught mussels collected from central California.

100 Quagga mussels collected within growing Cladophora beds in the

101 ional and sensory analysis of raw and cooked mussels comparing Mytilus sp. from the north-west coast

102 review highlights the bioactive potential of mussel components from species of the genus Mytilus (e.g

103 ot interact with activity level to influence mussel consumption, but independently reduced the slope

104 Mussel culture is frequently perceived as having little

105 At the same time as mussels declined, community composition shifted: at the

106 NA shedding was statistically similar across mussel densities, but that first-order decay constants v

107 be used as a complementary tool to estimate mussel density.

108 t DOC types were taken up in some measure by mussels, depending on the DOC types.

109 Awareness of mussel derived molecules, that promote health, has contr

110 g by deceiving the mechanosensing ability of mussels, deterring secretion of adhesive threads, and de

111 Recently, interest in mussel dietary supplements and functional foods has incr

112 olumn, of which 12 kg would be absorbed into mussel digestive systems.

113 hat selective feeding by invasive dreissenid mussels directly impacts the microbial component of the

114 e use of environmental DNA (eDNA) to monitor mussel distributions and diversity is a promising tool.

115 ger model set with these data and found that mussels do not Levy walk: Their movement is best describ

116 ails) on community recovery under both high (mussel dominated) and low flow (plant dominated) conditi

117 In areas of dense Cladophora and quagga mussel (Dreissena bugensis) assemblages, as well as in r

118 ly after the introduction of invasive quagga mussel (Dreissena rostriformis bugensis).

119 d detect the bioaccumulation of NPs in zebra mussels (Dreissena polymorpha) exposed for 1 h at enviro

120 The quagga mussel, Dreissena rostriformis bugensis, received maximu

121 yte in the methylated phenolic fraction of a mussel extract from a previous study.

122 he detection of saxitoxin both in buffer and mussel extracts in the range of 2.2-19.7 ng/mL (IC(20)-I

123 erved LOQs were 11.0, 9.6, and 2.4 ng/mL for mussel extracts, algal net samples and seawater, respect

124 ethylation, respectively, of the HPCs in the mussel extracts.

125 Mussel (family Mytilidae) production has doubled over th

126 This expansion includes mussels (family Mytilidae) where production currently st

127 nature of changes in benthos associated with mussel farming grab and video sampling around seven muss

128 cale benthic impacts these data suggest that mussel farming is a relatively benign way of producing f

129 There was no evidence that mussel farming was associated with changes in macrobenth

130 n sediment oxygenation in close proximity to mussel farms reported here suggests that farms located o

131 farming grab and video sampling around seven mussel farms was conducted.

132 ere taken remotely around a random sample of mussel farms, redox was measured at 10 mm sediment depth

133 Mussel flavoured GF bread can be included in the celiac

134 ces apparatus to investigate the adhesion of mussel foot protein 3 (Mfp3) "slow", a hydrophobic prote

135 For example, in mussel foot protein 3 slow (mfp-3s, one of two electroph

136 Marine mussels use catechol-rich interfacial mussel foot proteins (mfps) as primers that attach to mi

137 Mussel foot proteins (Mfps) exhibit remarkably adaptive

138 al underwater adhesives obtained from fusing mussel foot proteins (Mfps) of Mytilus galloprovincialis

139 The adhesion of mussel foot proteins (Mfps) to a variety of specially en

140 nslating sticky biological molecules-such as mussel foot proteins (MFPs)-into synthetic, cost-effecti

141 Mussel foot proteins provide insights about adhesive ada

142 through surface-water diffusivity, different mussel foot proteins were found to have different abilit

143 ypothesis proposed that large chemosynthetic mussels found at deep-sea hydrothermal vents descend fro

144 hat, at similar times of sale, biometrics of mussels from Armona and Vigo were similar and bigger tha

145 e a group of lipophilic toxins discovered in mussels from Ireland in 1995 following a human poisoning

146 assimilation efficiency (AE) of TiO2 NPs by mussels from their diet was very low (AE = 3.0 +/- 2.7%)

147 surviving cordgrass patches associated with mussels function as nuclei for vegetative re-growth and,

148 In natural beds, mussels generate self-organized patterns at two differen

149 is ecosystem service, provided by the ribbed mussel (Geukensia demissa), was studied in animals suspe

150 iological sequence sections extractable from mussel-glue proteins.

151 and quantification of vitellogenin in marine mussel gonads and compared the results with those obtain

152 rmation about Vtg levels, at least in marine mussel gonads.

153 Furthermore, mussels grown suspended in the water column contained su

154 Mussel growth occurs at a cost to the structural integri

155 Mussel growth was also indirectly related to tree radial

156 ) suggesting that NPs are mainly captured in mussel gut, with little penetration in their internal or

157 MSPD) for determination of nine triazines in mussels has been optimised in terms of the sorbents used

158 The adhesive system of marine mussels has been the focus of much attention in recent y

159 Mussels have a remarkable ability to attach their holdfa

160 At one contaminated site mussels have anomalously high delta(202)Hg, indicating e

161 esults of these comparisons showed that blue mussels have declined in the Gulf of Maine by >60% (rang

162 Mussels have evolved adaptations to stabilize Dopa again

163 clerotized cuticle and byssal threads of the mussel, have been shown to exhibit excellent mechanical

164 Mussel health status was investigated incorporating hist

165 Conversely, in low light mussels impeded nitrogen and energy metabolism, and enha

166 rimental samples, both assays detected zebra mussel in 94% of spiked samples and 0% of negative contr

167 Recent spread of invasive mussels in Lake Michigan has altered primary productivit

168 rs the infestation extent of invasive quagga mussels in the Great Lakes and is consistent with the de

169 Mytilus are edible mussels, including commercially-significant species such

170 The estimated toxin content per mussel increased substantially with the treatment, which

171 olymer network, demonstrating the utility of mussel-inspired bonding for processing a wide range of p

172 terials that are surface-functionalized with mussel-inspired catechols.

173 properties have been engineered by means of mussel-inspired metal-chelating catechol-functionalized

174 Translation of mussel-inspired wet adhesion typically entails catechol

175 Several sea otter and mussel isolates were highly related, suggesting that an

176 arious estuarine organisms (green crab, blue mussel, killifish, eider) to investigate methylmercury (

177 Field applications of U/Ca were tested with mussel larvae reared in situ at both known and unknown p

178 d organic carbon (DOC) on Cu accumulation on mussel larvae.

179 de Jager et al. concluded that mussels Levy walk.

180 of two southern and two hybridizing northern mussel lineages that exhibited a substantial, though inc

181 t reduction (50 mV) in redox adjacent to the mussel lines.

182 roximately 10 times as abundant close to the mussel-lines compared with 64 m distance.

183 In addition, mussel lipids, comprising polyunsaturated fatty acids (P

184 ied in homogenised mussel meat and 29 in the mussel liquor (i.e. the seawater enclosed in the mantle

185 In the mussel liquor, dimethyl sulphide was undetectable pre-st

186 Mussels live in stream sediments and can be challenging

187 cture varied in distinct ways in response to mussel loss, grazer loss, predator loss and with nutrien

188 roteins in the byssal adhesive plaque of the mussel M. edulis.

189 rty-four VOCs were identified in homogenised mussel meat and 29 in the mussel liquor (i.e. the seawat

190 Direct alkaline hydrolysis of the mussel meat yielded more toxin than the standard hydroly

191 The LOQ in seafood is 11 mug palytoxin/kg mussel meat, lower than that of the most common detectio

192 nge in relative concentration in homogenised mussel meat.

193 ns significantly exceeding that of analogous mussel-mimetic peptides.

194 Despite the growing number of mussel-mimicking polymers, there has been little effort

195 tern US coastline reveal spatially dispersed mussel mounds increased cordgrass survival during severe

196 emonstrates that the CCRW not only describes mussel movement patterns, it explains them.

197 Sessile marine mussels must "dry" underwater surfaces before adhering t

198 of a protease from the visceral mass of the mussel Mytella charruana as well as evaluation of its ab

199 tion of population abundance of the dominant mussel Mytilus californianus observed along the West Coa

200 bility of a critical foundation species, the mussel Mytilus californianus.

201 ken up into the cells and tissue of the blue mussel Mytilus edulis L.

202 ell as ingestion of pre-exposed food (common mussel Mytilus edulis).

203 the abundant and commercially important blue mussel Mytilus edulis.

204 boratory and field settings in larvae of the mussels Mytilus californianus and M. galloprovincialis.

205 s are consistent with recent observations of mussels Mytilus edulis and the Australian desert ant Mel

206 Blue mussel (Mytilus edulis L.) farming constitutes the large

207 ntified changes in the abundance of the blue mussel (Mytilus edulis), a foundation species known to i

208 r ~0.1 muM) in two keystone benthic species; mussels (Mytilus edulis) and purple sea urchins (Paracen

209 anic contaminants in their tissues than blue mussels (Mytilus edulis) collected at a nearby benthic s

210 describe accurately the movement patterns of mussels (Mytilus edulis) during spatial pattern formatio

211 uropean flat oysters (Ostrea edulis) or blue mussels (Mytilus edulis) in seawater to two different de

212 ine the arsenic species distribution in blue mussels (Mytilus edulis) obtained from an area where the

213 PCB concentrations in sediments and in blue mussels (Mytilus edulis; r = -0.33, p = 0.012), which is

214 ical relationship between copper toxicity to mussels (Mytilus sp.) and ambient dissolved organic carb

215 used to investigate the response of the blue mussel, Mytilus edulis, to a 90-day exposure to reduced

216 interactions between CeO2 ENMs and a marine mussel, Mytilus galloprovincialis, are affected through

217 at yield and water-holding capacity) of blue mussel, Mytilus galloprovincialis, reared in the North A

218 c (Zn), and copper (Cu) in the Mediterranean mussel, Mytilus galloprovincialis, was examined in Musse

219 and size of early life stages of two mytilid mussels, Mytilus californianus and M. galloprovincialis.

220 tidal cycle on the physiology of intertidal mussels, Mytilus californianus, by monitoring rhythms of

221 experiments indicate this positive effect of mussels on cordgrass was due to mounds enhancing water s

222 the group of proteins the focus is mainly on mussel peptides e.g. those obtained by bio-transformatio

223 se dissolved Cu species by the coastal green mussel Perna viridis was quantified for the first time.

224 Greenshell mussels (Perna canaliculus) were dry-stored at 6.44+/-0.

225 In mesocosm experiments, mussels, Perna viridis, were subjected to simulated clim

226 ly distinct interfacial adhesive proteins in mussel plaques), the high proportion of hydrophobic amin

227 m and muscle proteins, carbohydrates, algae, mussels, polydimethylsiloxane, polyethylene, polyoxymeth

228 Within the third group of carbohydrates, mussel polysaccharides are investigated.

229 of historical and contemporary baselines of mussel population abundance and dynamics in the Gulf of

230 ynchronized fluctuations in the abundance of mussel populations across a whole continent despite limi

231 The assumption that mussel populations are only connected via additional ste

232 some similarities in proximate composition, mussels presented differences in lipid classes, fatty ac

233 y related to three major chemical classes of mussel primary metabolites, i.e. proteins, lipids, and c

234 Mussels produce organic biodeposits which are dispersed

235 Green mussel protein hydrolysates (GMPH) utilization for the e

236 co-styrene] may be the strongest of reported mussel protein mimics.

237 is conspicuously sparing in the sequences of mussel proteins, exhibit reversible adhesion interaction

238 udied in animals suspended from a commercial mussel raft in the urban Bronx River Estuary, NY, in wat

239 esultant reduced crystallographic control in mussels raises concerns for shell protective function un

240 The mussels realise this Levy walk to good approximation acr

241 croalgal coverage at low flow sites and also mussel recovery at high flow sites.

242 ussels, and the subsequent detachment of the mussels returned bare rock again.

243 PCBs in duck mussels, roach, eel, pikeperch, perch and pike were most

244 g arsenobetaine may being used in all of the mussel's cells in a physiological function such as an in

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

246 -BDE194 was identified and quantified in new mussels, sampled in 2012 from two locations on the Swedi

247 the phenolic fraction of previously analyzed mussel samples after methylation of the halogenated phen

248 ly the method was applied to the analysis of mussel samples from Galicia (NW Spain).

249 Inter- and intra-assay studies of negative mussel samples spiked with various OA concentrations pro

250 Naturally-contaminated mussel samples were analysed and the results obtained sh

251 lucidation of the free fatty acid profile in mussel samples, avoiding a previous derivatization step,

252 were registered in some leafy vegetables and mussels samples, while high nitrites concentrations were

253 species, with partial detection in molluscs: mussels, scallops and snails but none in oyster, octopus

254 nce on the nAChR/microsphere-based assay for mussels, scallops, and clams.

255 ffects from the different samples evaluated (mussels, scallops, oysters, clams, cockles) nor interfer

256 Marine mussels secrete strong underwater adhesives that have be

257 tool, however, we need to know how much eDNA mussels shed into their environment and how long the eDN

258 is loss of structural integrity could impact mussel shell strength and reduce protection from predato

259 The best results were found when 0.5g mussel shell, 0.5g sodium sulfate and 5mL ethanol were u

260 Mussels showed an extracellular acidosis in response to

261 -increment width chronologies for freshwater mussel species in the Pacific Northwest, United States a

262 bility of larval exchange for two congeneric mussel species with overlapping but distinct distributio

263 esence/absence and abundance of a freshwater mussel species, Lampsilis siliquoidea.

264 ntiation in a mosaic hybrid zone between two mussel species, Mytilus edulis and M. galloprovincialis.

265 Under high light, mussels stimulated seagrass nitrogen and energy metaboli

266 ification affects interactions with juvenile mussels, such that thermal stresses and associated morta

267 rmation and less crystallographic control in mussels suggesting that ACC is used as a repair mechanis

268 -damage was four times lower in urchins than mussels, suggesting that internal acid-base regulation i

269 When prey were unable to disperse, TMIEs on mussel survival were 3 times higher than the DMIEs.

270 The effect of industrial steaming on mussels that had been naturally exposed to DSP toxins fo

271 s at high pH was similar to that from native mussel thread cuticle and the gels displayed elastic mod

272 62.6 kg of nitrogen would be sequestered in mussel tissue and shell.

273 ed did not result in significantly different mussel tissue or pseudofeces Ce concentrations.

274 fested ballast and harbor samples with zebra mussel tissue to further test each assay's detection cap

275 ied to different food samples (NIST SRM 2976 mussel tissue, pepper, ginger, wheat flour, red lentil,

276 The samples were mussel tissue, squid muscle, crab claw meat, whale meat,

277 for the sample with the lowest MMHg content, mussel tissue, with a HorRat value of 1.6.

278 e values in water (14.2+/-1.6%) and incurred mussel tissues (19.0+/-4.1%).

279 s (water), as well as in spiked and incurred mussel tissues to understand its fate in the food supply

280 trategies reported in organisms ranging from mussels to marine predators and monkeys, and CXCL10 aids

281 and soft materials at an 80:20 ratio enables mussels to rapidly and effectively dissipate impact ener

282 all species) and 13 breeding sampling areas (mussels) to assess As, Cd, Hg and Pb levels and the huma

283 the effects of climate change on determining mussel toxin-pathogen load in an ecologically relevant,

284 Marine mussels use catechol-rich interfacial mussel foot protei

285 zebra mussel was not detected, while quagga mussel was detected in all samples at a rate of 85% for

286 In unmanipulated samples, zebra mussel was not detected, while quagga mussel was detecte

287 The time-related metabolic signature of mussels was analysed by Orthogonal Partial Least Squares

288 gondii DNA and the presence of T. gondii in mussels was significantly associated with proximity to f

289 riled (IUCN listed as endangered) freshwater mussel, was examined to determine genetic diversity and

290 , Mytilus galloprovincialis, was examined in Mussel Watch (MW) databases of metal pollution at eighte

291 nd the 10-year historical data from the NOAA Mussel Watch program.

292 ant microbial groups involved in spoilage of mussels were also investigated.

293 g the concentrations reported in Baltic blue mussels were also studied.

294 om past French Navy activities, seawater and mussels were collected in Toulon Bay (NW Mediterranean S

295 tated reformation of small-scale patterns if mussels were dislodged.

296 these effects were virtually eliminated when mussels were exposed to both harmful microorganisms simu

297 arvesting time and location in Ireland, blue mussels were investigated for their biochemical composit

298 Naturally occurring populations of ribbed mussels were observed to be healthy and resilient in thi

299 cribed in this work, it can be expected that mussels with toxicities well below the regulatory limit

300 of microplastics by marine biota, including mussels, worms, fish, and seabirds, has been widely repo