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1 another item never encountered before (e.g. mussel).
2 ion exhibited by adhesion proteins of marine mussel.
3 ybean, pea, chlorella, spirulina, oyster and mussel.
4 ecies, Mytilus californianus, the California mussel.
5 and the filter-feeding behavior of the blue mussel.
6 inactivation of E. coli after uptake by the mussel.
7 on keystone species, such as the Baltic blue mussel.
8 g marsh cordgrass and aggregations of ribbed mussels.
9 we estimate chemical depuration kinetics for mussels.
10 reported within are the first for freshwater mussels.
11 within the soft adhesive produced by marine mussels.
12 d to that of biological adhesion, e.g., from mussels.
13 so in O. cf. ovata extracts and contaminated mussels.
14 stage of the colonization of invasive quagga mussels.
15 ological function and toxin-pathogen load in mussels.
16 bility but was unaffected by the presence of mussels.
17 reduced nutrient concentrations and invasive mussels.
18 al Ti background, which varied in individual mussels.
19 reissena bugensis) and zebra (D. polymorpha) mussels.
20 erred the evolution of effective adhesion by mussels.
21 e prevalence and genotype(s) of T. gondii in mussels.
22 nal content properties between the different mussels.
23 ting marine habitat contamination using wild mussels.
24 d problems in discrimination these in cooked mussels.
25 ured in mangrove sediments, clams, and caged mussels.
26 ) inhabiting the mantle cavity of freshwater mussels.
30 longest mussel chronologies (1982-2003; PC1(mussel)) accounted for 47% of the dataset variability an
32 This study expands the scope of translating mussel adhesion from simple Dopa-functionalization to mi
35 ationally modified amino acid dopa (DOPA) in mussel adhesion, catechol functional groups have become
39 2002/657/UE guidelines, and applied it to 50 mussel and 50 clam samples derived from various Food and
41 e that thermal buffering by centimetre-thick mussel and seaweed beds eliminates differences in stress
42 e molecular tools for T. gondii detection in mussels and (ii) apply optimized methods in a surveillan
43 ugar C-methyl-scyllo-inositol (mytilitol) in mussels and clams (Mytilus and Ruditapes spp., respectiv
44 (see phylogenetic tree; Figure 1); Bivalvia (mussels and clams), protected by shells and practically
47 eractions in the form of a mutualism between mussels and dominant cordgrass in salt marshes enhance e
48 tential to be a complementary tool to survey mussels and enhance current efforts to monitor and prote
50 onfirm the identity of this compound in blue mussels and investigate whether the analyte is diOH- and
51 shed a symbiosis with Bathymodiolus heckerae mussels and poecilosclerid sponges from asphalt-rich, de
52 Cyclic hydrocarbons were detected in dosed mussels and principle component analysis of gas chromato
56 for tracing the labels in aquatic (snail and mussel) and terrestrial (earthworm) organisms and for mo
58 a good proxy to assess Vtg levels in marine mussels, and careful verification of the adequacy of the
59 s and crustose algae, they were overgrown by mussels, and the subsequent detachment of the mussels re
60 evant physical and nutritional attributes of mussels, and then we use economic discrete choice models
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
65 umer exposure to TiO(2)NPs when contaminated mussels are consumed without a proper depuration process
72 urthermore, the importance of monitoring the mussel as food material in respect to contaminations wit
75 spatial scales: regularly spaced clusters of mussels at centimeter scale driven by behavioral aggrega
78 fused coatings exhibit very low preferential mussel attachment and ultralow adhesive strengths under
79 somallon squamiferum and Gigantopelta aegis, mussel Bathymodiolus marisindicus, and Neolepas sp. stal
80 connectivity of ecologically important vent mussels (Bathymodiolus spp.) from the Mid-Atlantic Ridge
81 e two spatial scales of self-organization on mussel bed persistence, we conducted field manipulations
84 edulis) during spatial pattern formation in mussel beds can be regarded as being the first three lev
92 age, sponge spicules) to attachment devices (mussel byssal threads), from both invertebrate and verte
94 ates of DOPA residues in proteins comprising mussel byssus fibers before, during, and after protein s
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
101 ional and sensory analysis of raw and cooked mussels comparing Mytilus sp. from the north-west coast
102 31-1778 ug/kg) and in ionic titanium treated mussels (concentration 1574 ug/kg), suggesting potential
103 ICP-MS revealed NPs in both TiO(2)NP treated mussels (concentration range: 231-1778 ug/kg) and in ion
104 ot interact with activity level to influence mussel consumption, but independently reduced the slope
106 NA shedding was statistically similar across mussel densities, but that first-order decay constants v
110 g by deceiving the mechanosensing ability of mussels, deterring secretion of adhesive threads, and de
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 Southeast Asia is a species-rich freshwater mussel diversity hotspot with numerous local endemic spe
117 In areas of dense Cladophora and quagga mussel (Dreissena bugensis) assemblages, as well as in r
119 d detect the bioaccumulation of NPs in zebra mussels (Dreissena polymorpha) exposed for 1 h at enviro
120 sed on whether the grazing activity of zebra mussels (Dreissena polymorpha) would result in a consist
123 udy evaluated the response of the freshwater mussel, Elliptio complanata, after exposure to produced
124 We show that the association with freshwater mussels evolved independently in three leech clades, i.e
125 ern biogeographic barrier between freshwater mussel faunas of the Western Indochina and Sundaland sub
127 accumulate in the soft tissue of freshwater mussels following exposure to diluted oil and gas produc
130 Marine mussels use catechol-rich interfacial mussel foot proteins (mfps) as primers that attach to mi
133 nslating sticky biological molecules-such as mussel foot proteins (MFPs)-into synthetic, cost-effecti
135 ntury, highlighting a protective capacity of mussels for qualitative and quantitative trade-offs in b
136 ypothesis proposed that large chemosynthetic mussels found at deep-sea hydrothermal vents descend fro
137 hat, at similar times of sale, biometrics of mussels from Armona and Vigo were similar and bigger tha
139 d mussels) than controls (apparently healthy mussels from the same or matched sites), and cases had 2
140 assimilation efficiency (AE) of TiO2 NPs by mussels from their diet was very low (AE = 3.0 +/- 2.7%)
141 surviving cordgrass patches associated with mussels function as nuclei for vegetative re-growth and,
143 is ecosystem service, provided by the ribbed mussel (Geukensia demissa), was studied in animals suspe
145 and quantification of vitellogenin in marine mussel gonads and compared the results with those obtain
149 ) suggesting that NPs are mainly captured in mussel gut, with little penetration in their internal or
150 t in axenic mixed species co-cultures, zebra mussels had a significantly greater negative effect on S
151 MSPD) for determination of nine triazines in mussels has been optimised in terms of the sorbents used
152 esults of these comparisons showed that blue mussels have declined in the Gulf of Maine by >60% (rang
154 an in mussels (p-value < 0.001), with Danish mussels having the highest mytilitol concentration.
156 rimental samples, both assays detected zebra mussel in 94% of spiked samples and 0% of negative contr
157 ectious causes of these declines, we studied mussels in Clinch River, Virginia and Tennessee, USA, wh
159 rs the infestation extent of invasive quagga mussels in the Great Lakes and is consistent with the de
164 olymer network, demonstrating the utility of mussel-inspired bonding for processing a wide range of p
166 omers, butyl acrylate and acrylic acid, with mussel-inspired lysine- and aromatic-rich monomers.
173 of two southern and two hybridizing northern mussel lineages that exhibited a substantial, though inc
175 h species likely arose in a third species of mussel (M. trossulus), but these cancer cells are indepe
176 en alpha-CAs were found in the Mediterranean mussel mantle and the most abundant form was named, MgNA
179 tern US coastline reveal spatially dispersed mussel mounds increased cordgrass survival during severe
180 of a protease from the visceral mass of the mussel Mytella charruana as well as evaluation of its ab
182 d exceptional archival specimens of the blue mussel Mytilus edulis collected regularly between 1904 a
184 ivalves-the oyster Crassostrea gigas and the mussel Mytilus edulis-over 10 years (2009-2018) in a Fre
187 ysed the fine-scale genetic structure in the mussel Mytilus galloprovincialis using a few ancestry-in
188 Mytilipin B, isolated in 2002 from culinary mussel Mytilus galloprovincialis, whose initially propos
189 boratory and field settings in larvae of the mussels Mytilus californianus and M. galloprovincialis.
191 oncentrations of UV filters in raft cultured mussel ( Mytilus galloprovincialis) of the estuary Ria d
193 ntified changes in the abundance of the blue mussel (Mytilus edulis), a foundation species known to i
194 l mineralization in the marine Mediterranean mussel (Mytilus galloprovincialis) we characterized them
195 ically distant populations of two species of mussels (Mytilus chilensis in South America and M. eduli
196 r ~0.1 muM) in two keystone benthic species; mussels (Mytilus edulis) and purple sea urchins (Paracen
197 anic contaminants in their tissues than blue mussels (Mytilus edulis) collected at a nearby benthic s
198 describe accurately the movement patterns of mussels (Mytilus edulis) during spatial pattern formatio
199 uropean flat oysters (Ostrea edulis) or blue mussels (Mytilus edulis) in seawater to two different de
200 PCB concentrations in sediments and in blue mussels (Mytilus edulis; r = -0.33, p = 0.012), which is
201 ical relationship between copper toxicity to mussels (Mytilus sp.) and ambient dissolved organic carb
202 used to investigate the response of the blue mussel, Mytilus edulis, to a 90-day exposure to reduced
203 oot proteins (Mfp) secreted by the saltwater mussel, Mytilus galloprovincialis and by recent advances
204 at yield and water-holding capacity) of blue mussel, Mytilus galloprovincialis, reared in the North A
206 ern oysters, Crassostrea virginica, and blue mussels, Mytilus edulis, were offered variously sized po
208 experiments indicate this positive effect of mussels on cordgrass was due to mounds enhancing water s
209 ben, diclofenac, and triclosan) from exposed mussels on the basis of the Versantvoort's fed-state phy
211 ded with 250 mg of freeze-dried and powdered mussel onto a polyvinyldiene difluoride filter membrane.
213 t to be significantly lower in clams than in mussels (p-value < 0.001), with Danish mussels having th
214 the group of proteins the focus is mainly on mussel peptides e.g. those obtained by bio-transformatio
217 ly distinct interfacial adhesive proteins in mussel plaques), the high proportion of hydrophobic amin
218 m and muscle proteins, carbohydrates, algae, mussels, polydimethylsiloxane, polyethylene, polyoxymeth
221 of historical and contemporary baselines of mussel population abundance and dynamics in the Gulf of
223 some similarities in proximate composition, mussels presented differences in lipid classes, fatty ac
224 y related to three major chemical classes of mussel primary metabolites, i.e. proteins, lipids, and c
225 polar, and Baltic low-salinity environments, mussels produced thin shells with a thicker external org
226 cation decreased towards high latitude, with mussels producing thinner shells with a higher organic c
228 is conspicuously sparing in the sequences of mussel proteins, exhibit reversible adhesion interaction
230 udied in animals suspended from a commercial mussel raft in the urban Bronx River Estuary, NY, in wat
231 esultant reduced crystallographic control in mussels raises concerns for shell protective function un
235 sted solid-liquid extraction of the original mussel sample and the residual (nonbioaccessible) fracti
236 -BDE194 was identified and quantified in new mussels, sampled in 2012 from two locations on the Swedi
237 the phenolic fraction of previously analyzed mussel samples after methylation of the halogenated phen
241 lucidation of the free fatty acid profile in mussel samples, avoiding a previous derivatization step,
242 cal protein adhesives, which are secreted by mussels, sandcastle worms, barnacles, and caddisfly larv
243 ffects from the different samples evaluated (mussels, scallops, oysters, clams, cockles) nor interfer
246 tool, however, we need to know how much eDNA mussels shed into their environment and how long the eDN
247 effects of salinity and food availability on mussel shell composition predict the deposition of a thi
248 st predictor of within-region differences in mussel shell deposition, mineral and organic composition
251 rns on the rocks and accumulations of broken mussel shells, all fractured in a characteristic way, be
255 -increment width chronologies for freshwater mussel species in the Pacific Northwest, United States a
257 ntiation in a mosaic hybrid zone between two mussel species, Mytilus edulis and M. galloprovincialis.
259 ification affects interactions with juvenile mussels, such that thermal stresses and associated morta
260 rmation and less crystallographic control in mussels suggesting that ACC is used as a repair mechanis
261 -damage was four times lower in urchins than mussels, suggesting that internal acid-base regulation i
262 s more likely to be found in cases (moribund mussels) than controls (apparently healthy mussels from
264 materials of oyster tissue (NIST 1566b) and mussel tissue (NIST 2977), and the results were statisti
267 fested ballast and harbor samples with zebra mussel tissue to further test each assay's detection cap
269 ied to different food samples (NIST SRM 2976 mussel tissue, pepper, ginger, wheat flour, red lentil,
273 s (water), as well as in spiked and incurred mussel tissues to understand its fate in the food supply
276 An in vivo study was conducted by exposing mussels to different concentrations of TiO(2)NPs (0.25 m
277 all species) and 13 breeding sampling areas (mussels) to assess As, Cd, Hg and Pb levels and the huma
278 the effects of climate change on determining mussel toxin-pathogen load in an ecologically relevant,
283 the effects of climate change on Baltic blue mussels using a 17-year dataset on population density.
284 zebra mussel was not detected, while quagga mussel was detected in all samples at a rate of 85% for
286 The time-related metabolic signature of mussels was analysed by Orthogonal Partial Least Squares
287 gondii DNA and the presence of T. gondii in mussels was significantly associated with proximity to f
288 riled (IUCN listed as endangered) freshwater mussel, was examined to determine genetic diversity and
291 om past French Navy activities, seawater and mussels were collected in Toulon Bay (NW Mediterranean S
293 these effects were virtually eliminated when mussels were exposed to both harmful microorganisms simu
295 arvesting time and location in Ireland, blue mussels were investigated for their biochemical composit
296 ry, ancient and modern shells of limpets and mussels were isotopically analysed to explore changes in
297 Naturally occurring populations of ribbed mussels were observed to be healthy and resilient in thi
298 ation mechanisms, that is, the Cu-regulating mussels with almost constant Cu concentrations and the C
299 s are willing to pay on average 52% less for mussels with evidences of OA and are willing to increase
300 cribed in this work, it can be expected that mussels with toxicities well below the regulatory limit