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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.
27                                     Thirteen mussels (1.4%) had detectable T. gondii DNA and the pres
28 when subjected to feeding pressure by quagga mussels, a widespread aquatic invasive species.
29 pecies richness was positively correlated to mussel abundance in mid to high intertidal zones.
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  This study expands the scope of translating mussel adhesion from simple Dopa-functionalization to mi
33 f macromolecules to mimic complex aspects of mussel adhesion still constitutes a challenge.
34 umerous attempts have been made to translate mussel adhesion to diverse synthetic platforms.
35 ationally modified amino acid dopa (DOPA) in mussel adhesion, catechol functional groups have become
36 of a carbon nanotube (CNT) fiber inspired by mussel-adhesion chemistry is described.
37 ol-metal ion coordination chemistry found in mussel adhesive proteins is developed.
38 r dimension in designing synthetic mimics of mussel adhesive proteins.
39 2002/657/UE guidelines, and applied it to 50 mussel and 50 clam samples derived from various Food and
40 (tuna and plaice) but decreased in molluscs (mussel and octopus).
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
45                         Filter feeders, like mussels and clams, are suitable bioindicators of environ
46 geographic-dependent content of mytilitol in mussels and clams.
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
49 rine natural products that are isolated from mussels and freshwater algae.
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
53 lorinated biphenyls (PCBs) concentrations in mussels and sediments.
54 ples from aquaculture facilities, wild grown mussels and waste material.
55                                          PC1(mussel) and PC1(discharge) were closely linked to region
56 for tracing the labels in aquatic (snail and mussel) and terrestrial (earthworm) organisms and for mo
57 bitats for over 60% of North America's fish, mussel, and crayfish species.
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
64                       Adhesive proteins from mussels are biocompatible and elicit only minimal immune
65 umer exposure to TiO(2)NPs when contaminated mussels are consumed without a proper depuration process
66                                   Freshwater mussels are ecosystem engineers and keystone species in
67                                              Mussels are opportunistic macrofouling organisms that ca
68                                   Freshwater mussels are sensitive to habitat and water quality, reve
69   However, biological threats for freshwater mussels are still poorly known.
70                                   Freshwater mussels are vital components of stream ecosystems, yet r
71 rs and assays targeting the Freshwater Pearl Mussel as a model organism.
72 urthermore, the importance of monitoring the mussel as food material in respect to contaminations wit
73                                        Seven mussel-associated leech species and two additional free-
74                          So far, examples of mussel-associated leech species are recorded from East A
75 spatial scales: regularly spaced clusters of mussels at centimeter scale driven by behavioral aggrega
76 levels that are rather variable among female mussels at different stages of gonad development.
77              We observed sea otters pounding mussels at the Bennett Slough Culverts site, California,
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
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 nt efforts to monitor and protect freshwater mussel biodiversity.
87 smission widespread in gonochoric freshwater mussels (Bivalvia: Palaeoheterodonta: Unionida).
88       The systematics of Oriental freshwater mussels (Bivalvia: Unionidae) is poorly known.
89 ty level, on the crab functional response to mussel (Brachidontes exustus) prey.
90  dioxide nanoparticles (TiO(2)NPs) in edible mussels bred in polluted artificial seawater.
91      The outstanding adhesive performance of mussel byssal threads has inspired materials scientists
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 ates of DOPA residues in proteins comprising mussel byssus fibers before, during, and after protein s
95                                          The mussel byssus has long been a source of inspiration for
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 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
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 87) around the relationship between eDNA and mussel density in mesocosms.
108  be used as a complementary tool to estimate mussel density.
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  Southeast Asia is a species-rich freshwater mussel diversity hotspot with numerous local endemic spe
116  1900 to further understanding of freshwater mussel diversity in the region.
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 sed on whether the grazing activity of zebra mussels (Dreissena polymorpha) would result in a consist
121                                   The quagga mussel, Dreissena rostriformis bugensis, received maximu
122                                 Nonetheless, mussels eliminated more than 70% of the TiO(2)NPs after
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
126                                              Mussel flavoured GF bread can be included in the celiac
127  accumulate in the soft tissue of freshwater mussels following exposure to diluted oil and gas produc
128                              For example, in mussel foot protein 3 slow (mfp-3s, one of two electroph
129                                  Inspired by mussel foot proteins (Mfp) secreted by the saltwater mus
130 Marine mussels use catechol-rich interfacial mussel foot proteins (mfps) as primers that attach to mi
131                                              Mussel foot proteins (Mfps) exhibit remarkably adaptive
132 droxyphenylalanine (DOPA, Y) residues in the mussel foot proteins (Mfps) has been highlighted.
133 nslating sticky biological molecules-such as mussel foot proteins (MFPs)-into synthetic, cost-effecti
134                                              Mussel foot proteins provide insights about adhesive ada
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
138 pecies and four new subspecies of freshwater mussels from Myanmar.
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,
142                             In natural beds, mussels generate self-organized patterns at two differen
143 is ecosystem service, provided by the ribbed mussel (Geukensia demissa), was studied in animals suspe
144 iological sequence sections extractable from mussel-glue proteins.
145 and quantification of vitellogenin in marine mussel gonads and compared the results with those obtain
146 rmation about Vtg levels, at least in marine mussel gonads.
147                                 Furthermore, mussels grown suspended in the water column contained su
148                                              Mussel growth was also indirectly related to tree radial
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
153                                              Mussels have evolved adaptations to stabilize Dopa again
154 an in mussels (p-value < 0.001), with Danish mussels having the highest mytilitol concentration.
155                     Conversely, in low light mussels impeded nitrogen and energy metabolism, and enha
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
158                    Recent spread of invasive mussels in Lake Michigan has altered primary productivit
159 rs the infestation extent of invasive quagga mussels in the Great Lakes and is consistent with the de
160        Experiments were conducted using live mussels in which seawater iron levels were deficient, no
161                           Mytilus are edible mussels, including commercially-significant species such
162              The estimated toxin content per mussel increased substantially with the treatment, which
163                                              Mussel-inspired adhesives containing paired catechol and
164 olymer network, demonstrating the utility of mussel-inspired bonding for processing a wide range of p
165 terials that are surface-functionalized with mussel-inspired catechols.
166 omers, butyl acrylate and acrylic acid, with mussel-inspired lysine- and aromatic-rich monomers.
167 n and the long-term stability/performance of mussel-inspired polymers.
168                                    Herein, a mussel-inspired strategy is developed to yield silver-de
169 luding opto-bioelectronics, nanomedicine and mussel-inspired surface coating.
170                               Translation of mussel-inspired wet adhesion typically entails catechol
171 d organic carbon (DOC) on Cu accumulation on mussel larvae.
172                              With freshwater mussel life expectancy ranging from a few years up to 20
173 of two southern and two hybridizing northern mussel lineages that exhibited a substantial, though inc
174                                              Mussels live in stream sediments and can be challenging
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
177            Direct alkaline hydrolysis of the mussel meat yielded more toxin than the standard hydroly
178 ns significantly exceeding that of analogous mussel-mimetic peptides.
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
181 bility of a critical foundation species, the mussel Mytilus californianus.
182 d exceptional archival specimens of the blue mussel Mytilus edulis collected regularly between 1904 a
183 ell as ingestion of pre-exposed food (common mussel Mytilus edulis).
184 ivalves-the oyster Crassostrea gigas and the mussel Mytilus edulis-over 10 years (2009-2018) in a Fre
185 the abundant and commercially important blue mussel Mytilus edulis.
186                            The Mediterranean mussel Mytilus galloprovincialis is an ecologically and
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.
190 e change in critical foundation species, the mussels Mytilus edulis and M. trossulus.
191 oncentrations of UV filters in raft cultured mussel ( Mytilus galloprovincialis) of the estuary Ria d
192                                         Blue mussel (Mytilus edulis L.) farming constitutes the large
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
205  to reduced seawater pH in the Mediterranean mussel, Mytilus galloprovincialis.
206 ern oysters, Crassostrea virginica, and blue mussels, Mytilus edulis, were offered variously sized po
207 scribe 12 species and 4 genera of freshwater mussels new to science.
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
210             We show that sea otters pounding mussels on tidally emergent rocks leave distinct materia
211 ded with 250 mg of freeze-dried and powdered mussel onto a polyvinyldiene difluoride filter membrane.
212                                   Freshwater mussels (order Unionida) are among the world's most biod
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
215                              The Asian green mussel Perna viridis secretes several byssal plaque prot
216                     In mesocosm experiments, mussels, Perna viridis, were subjected to simulated clim
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
219         Inspired by the adhesive proteins of mussels, polydopamine (pDA) has emerged as one of the mo
220     Within the third group of carbohydrates, mussel polysaccharides are investigated.
221  of historical and contemporary baselines of mussel population abundance and dynamics in the Gulf of
222                          The assumption that mussel populations are only connected via additional ste
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
227                                        Green mussel protein hydrolysates (GMPH) utilization for the e
228 is conspicuously sparing in the sequences of mussel proteins, exhibit reversible adhesion interaction
229                                    The zebra mussels' putative preference for Synechocystis over Chlo
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
232                                          The mussels realise this Levy walk to good approximation acr
233 ussels, and the subsequent detachment of the mussels returned bare rock again.
234  from the European southwest coast (oysters, mussels, salmon organs, glass eels).
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
238 vity studies were also performed with spiked mussel samples and other interfering species.
239 ly the method was applied to the analysis of mussel samples from Galicia (NW Spain).
240                       Naturally-contaminated mussel samples were analysed and the results obtained sh
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
244                                       Marine mussels secret catechol-containing adhesive proteins tha
245                                       Marine mussels secrete proteins rich in residues containing cat
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
249 mology with oyster nacreins likely regulates mussel shell production.
250        The best results were found when 0.5g mussel shell, 0.5g sodium sulfate and 5mL ethanol were u
251 rns on the rocks and accumulations of broken mussel shells, all fractured in a characteristic way, be
252                                      Exposed mussels showed accumulation of Ba in the soft tissue sev
253                                              Mussels showed an extracellular acidosis in response to
254                               Interestingly, mussels showed wider amplitudes in the isotope variation
255 -increment width chronologies for freshwater mussel species in the Pacific Northwest, United States a
256 esence/absence and abundance of a freshwater mussel species, Lampsilis siliquoidea.
257 ntiation in a mosaic hybrid zone between two mussel species, Mytilus edulis and M. galloprovincialis.
258                            Under high light, mussels stimulated seagrass nitrogen and energy metaboli
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
263         The effect of industrial steaming on mussels that had been naturally exposed to DSP toxins fo
264  materials of oyster tissue (NIST 1566b) and mussel tissue (NIST 2977), and the results were statisti
265  62.6 kg of nitrogen would be sequestered in mussel tissue and shell.
266 ed did not result in significantly different mussel tissue or pseudofeces Ce concentrations.
267 fested ballast and harbor samples with zebra mussel tissue to further test each assay's detection cap
268 Tort-3 (Lobster hepatopancreas), ERM-CE 278 (mussel tissue) and Dolt-4 (Fish liver).
269 ied to different food samples (NIST SRM 2976 mussel tissue, pepper, ginger, wheat flour, red lentil,
270                             The samples were mussel tissue, squid muscle, crab claw meat, whale meat,
271 for the sample with the lowest MMHg content, mussel tissue, with a HorRat value of 1.6.
272 e values in water (14.2+/-1.6%) and incurred mussel tissues (19.0+/-4.1%).
273 s (water), as well as in spiked and incurred mussel tissues to understand its fate in the food supply
274                Exposure of the Mediterranean mussel to reduced water salinity (18 vs 37 ppt), caused
275  proteins, molecules that help anchoring the mussel to surfaces.
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,
279                                   Freshwater mussels (Unionida) are one of the most imperiled animal
280                            We use freshwater mussels (Unionidae) as a model to reconstruct spatial pa
281 itochondrial gene order among the freshwater mussels (Unionoidea).
282                                       Marine mussels use catechol-rich interfacial mussel foot protei
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
285              In unmanipulated samples, zebra mussel was not detected, while quagga mussel was detecte
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
289 ant microbial groups involved in spoilage of mussels were also investigated.
290 g the concentrations reported in Baltic blue mussels were also studied.
291 om past French Navy activities, seawater and mussels were collected in Toulon Bay (NW Mediterranean S
292 tated reformation of small-scale patterns if mussels were dislodged.
293 these effects were virtually eliminated when mussels were exposed to both harmful microorganisms simu
294                    A limited number of adult mussels were grown over an 8-week period in tanks dosed
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

 
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