ライフサイエンスコーパス: beach

1 orizing a scene as open, as outdoor, or as a beach.

2 ts popular, but chronically FIB-contaminated beach.

3 sources, varying by date, occurred at every beach.

4 ronounced as the herd spent more time on the beach.

5 ainment of pollution at a wave-dominant open beach.

6 n 1 Hz Rayleigh wave phase speed map of Long Beach.

7 in the upper 50 cm of a North Florida sandy beach.

8 scribed hatchling production at each nesting beach.

9 +/- 347.3 items/m(2)) on the surface of the beaches.

10 (Posidonia oceanica) found on Mediterranean beaches.

11 e of multiple contamination sources at these beaches.

12 en addressed in the intertidal zone of sandy beaches.

13 harge may be more important for coarser sand beaches.

14 levels of indicator bacteria at recreational beaches.

15 females to a series of predictably different beaches.

16 e best performing model types for California beaches.

17 ewport Bay and other urban-impacted enclosed beaches.

18 ntrollable, fecal source to suburban coastal beaches.

19 ace waters and tar balls from Gulf of Mexico beaches.

20 edunes are found on dissipative (reflective) beaches.

21 cretion along adjacent upcoast and downcoast beaches.

22 pathogens within bed sediment at freshwater beaches.

23 l samples collected from four Gulf of Mexico beaches 12-19 months after the Deepwater Horizon disaste

24 ing 64 of the 83 recaptured turtles to natal beaches (77.1%).

25 easurements that show patterns and trends of beach accretion following the restoration of sediment su

26 etections were more numerous when the EC/ENT Beach Action Value (but not when the Geometric Mean and

27 The "beach action value" was exceeded most often when using E

28 measurements taken at times of peak landing beach activity indicated that the highest proportion of

29 richia coli and enterococci, trigger coastal beach advisories and signal public health risks.

30 measured throughout the summer, resulting in beach advisories with social and economic consequences.

31 tatistical regression models used to predict beach advisories.

32 ncrease illness risks for swimmers and cause beach advisories.

33 days was found to be sufficient to trigger a beach advisory if eroded to surface water.

34 mechanism facilitating the recovery of sandy beaches after oil contamination.

35 ng advisories due to FIB contamination at 25 beaches along the California coastline.

36 Enclosed beaches along urban coastlines are frequent hot spots of

37 es are key ecosystem drivers in marine sandy beaches, an important and dynamic environment; however,

38 abate gulls using a falconry program for the beach and an upland landfill.

39 of nests or reproductive females at nesting beaches and (ii) ignorance of factors regulating recruit

40 etlands, such as marshes and mangroves, sand beaches and dunes, seagrass beds, and coral and oyster r

41 ings of small turtles downcurrent of nesting beaches and in association with drifting organisms (e.g.

42 Results were highly variable among beaches and matrices; some correlations with environment

43 terial collected to determine the age of the beaches and reconstruct postglacial relative sea level c

44 ly, of the total debris mass), while leeward beaches and the seafloor debris consisted of less weathe

45 and removal of plastic particles because of beaching and sinking.

46 rsus usual care (5 Atkins, 4 WW, and 1 South Beach) and 2 head-to-head (1 of Atkins, WW, and Zone, an

47 densities, (b) nest elevation by species and beach, and (c) estimated proportion of nests inundated u

48 in the surf zone, sand, and wrack at Cowell Beach, and ruled out the storm drain, the river, the har

49 ze the scenes they encounter: an office, the beach, and so on.

50 scored crowding at all surveyed fish landing beaches, and identified potential "hotspots" for disease

51 ands (sea surface, windward beaches, leeward beaches, and seafloor) to better describe sources and fa

52 merical model whereby FIB are delivered to a beach aquifer by wave-induced infiltration across the be

53 Simulated transport of E. coli in a beach aquifer is complex and does not correlate with con

54 lations indicate FIB rapidly accumulate in a beach aquifer with FIB primarily associated with sand ra

55 he accumulation and distribution of FIB in a beach aquifer.

56 mulate As, creating a risk of high As in the beach aquifer.

57 g the mobility of arsenic (As) in freshwater beach aquifers.

58 tribution in various matrices at Great Lakes beaches are limited.

59 xyhydrocarbons" in sand patties deposited on beaches are not well-known.

60 familiar surface gravity waves that break on beaches, are ubiquitous in the ocean.

61 Beaches around the world continuously adjust to daily an

62 each sand, emphasizing the role of the sandy beach as an aerobic biocatalytical reactor at the land-o

63 al indicators of fecal pollution rank Cowell Beach as the most polluted beach in California.

64 es (Caretta caretta), which leave their home beaches as hatchlings and migrate across entire ocean ba

65 hosphatase 2A, and the yeast kinase TOR1) or BEACH (beige and Chediak-Higashi) domains.

66 We found that neurons lacking the BEACH (beige-Chediak/Higashi) domain protein Neurobeachi

67 extracted from coastal barrier stratigraphy, beach berm and dune-beach contact.

68 ice outpatient dermatology office in Newport Beach (CA, USA).

69 ion subsurface geophysical structure in Long Beach, CA, from seismic noise recorded on a "large-N" ar

70 journeys around 16 locations throughout Long Beach, California and trained four machine learning mode

71 the seismogenic root of the NIF beneath Long Beach, California, and identify seismicity in an activel

72 d motions from the 11 March 1933 Mw 6.4 Long Beach, California, earthquake, the largest known earthqu

73 We find that HWEs overtopping the beach can be modeled as a marked Poisson process with ex

74 Fecal pollution at beaches can pose a health risk to recreators.

75 ere regionally consistent (up to 40 km), but beach catchment variables (drains/creeks, impervious sur

76 es around the globe and highlights how local beach characteristics can drive incubation temperatures.

77 mental factors, providing a flawed basis for beach closure decisions.

78 ble for runoff-associated inland and coastal beach closures) in stormwater biofilters (a common type

79 ions resulting in more accurate estimates of beach closures.

80 elevated As concentrations observed at both beaches, combined with the distribution of other dissolv

81 rrence, and microbial sources at Great Lakes beaches comes largely from individual beach studies.

82 Coastal dunes protect beach communities and ecosystems from rising seas and st

83 g intensified wave conditions at a fine sand beach, comparative characterization of the E. coli distr

84 Beach conditions were followed for three years after imp

85 For certain beach conditions, the amount of FIB accumulated in sand

86 To improve beach conservation efforts, current and future shoreline

87 al barrier stratigraphy, beach berm and dune-beach contact.

88 indings show that current research regarding beach debris requires significant improvement and standa

89 red to the environmental baseline of plastic beach debris.

90 ions remained unmet at a southern California beach despite a suite of management actions carried out

91 more plastic pollution (g/m(2)) than leeward beaches, despite smaller human populations on windward s

92 We show that GPS-causing mutations in its BEACH domain have profound and possible effects on the i

93 identify the large and poorly characterized BEACH domain protein Neurobeachin-like (NBEAL) 1 as a Go

94 Mutations in the BEACH domain resulted in formation of normal or slightly

95 to the family of beige and Chediak-Higashi (BEACH) domain proteins.

96 at three types of Beige and Chediak-Higashi (BEACH)-domain proteins contribute to both vacuolar prote

97 e results suggest that a cascade of multiple BEACH-domain proteins contributes to vacuolar protein tr

98 e a putative protein belonging to group D of BEACH-domain proteins, which possess kinase domains.

99 ed gene neurobeachin (nbea), which encodes a BEACH-domain-containing protein implicated in endomembra

100 r to the development of stochastic models of beach, dune, and barrier dynamics, as well as a better u

101 IIV on predator-prey interaction outcomes in beach-dwelling jumping spiders (Terralonus californicus)

102 a: see text] Furthermore, the characteristic beach elevation at any given location seems to be tied t

103 Disruption of other BEACH-encoding loci in the gfs12 mutant showed that BEAC

104 st Coast, corresponding to anomalously large beach erosion across the region.

105 des, waves, storms, and coastal change (i.e. beach erosion and cliff retreat).

106 llness for Campylobacter jejuni at the study beaches, especially where recreational water quality cri

107 ion is the result of thinning of cliff-front beaches, exacerbated by regional storminess and anthropo

108 and E. coli was transported deeper below the beach face.

109 ves on subsurface salinity distribution on a beach face.

110 ifer by wave-induced infiltration across the beach face.

111 d, Aylan Kurdi, lying face-down on a Turkish beach, filled the front pages of newspapers worldwide.

112 eposited in the swash zone on Gulf of Mexico beaches following the Deepwater Horizon oil spill.

113 All participants remained at a sunny beach for 3(1/2) hours at midday.

114 Using genetics, we identified natal beaches for 288 turtles that were live-captured off the

115 these methods has not been examined at most beaches for expectation of health risk and management de

116 nge of images that we might categorize as a "beach", for example, some will be more representative of

117 morphology of former shorelines preserved in beach-foredune ridges (BFR) within a protected embayment

118 Here, we used field data on an estuarine beach foreshore with numerical simulations to show that

119 ss spectroscopy (SIMS) analyses performed on Beach Formation muddy storm event beds reveal spatially

120 rdovician storm-dominated delta (Tremadocian Beach Formation, Bell Island Group, Newfoundland).

121 s (3 genera, at least 8 species) on adjacent beaches from 1900 to 2012, to help assess population sta

122 0%, respectively, in samples collected along beaches from April 2011 through August 2012.

123 collected 36 intertidal samples at 12 sandy beaches from four regions that spanned distances from 0.

124 f causing water quality and health risks for beach-goers.

125 l feedbacks in grasslands, facilitation in a beach grass community, and niche differences with indepe

126 The findings suggest that beach grooming for wrack removal is not justified as a m

127 Beach grooming was generally associated with either no c

128 The impacts of beach grooming, to remove wrack, were investigated at Co

129 Windward beaches had 1-2 orders of magnitude more plastic polluti

130 All beaches had detections of human and bovine viruses and p

131 Of these locations, Jupiter Florida/Vero Beach has the highest settlement rate in the model and i

132 factor affecting beach water quality, while beaches having a deteriorating water quality trend or lo

133 m of rip currents, thus posing an unexpected beach hazard that, to date, has been ignored.

134 ncoding loci in the gfs12 mutant showed that BEACH homologs acted in a cascading manner for PSV traff

135 pistatic genetic interactions observed among BEACH homologs were also found in the ETI responses of t

136 ) of DWH oil buried in a North Florida sandy beach, (ii) elucidated the long-term succession of the m

137 immunoconversions) in visitors to a tropical beach impacted by a publicly owned treatment works (POTW

138 ected during a predominantly dry summer at a beach impacted by nonpoint source pollution.

139 cooperative modeling approach for freshwater beaches impacted by point sources in which insights deri

140 y 30,000 animals along approximately 1 km of beach in 2011.

141 ctions among 483 visitors to a Lake Michigan beach in 2015.

142 ution rank Cowell Beach as the most polluted beach in California.

143 to remove wrack, were investigated at Cowell Beach in Santa Cruz, California using a long-term survey

144 sex and age of walruses hauled out on Alaska beaches in 2010-2011.

145 Here, using yearlong data sets measured at beaches in Alaska Prince William Sound, we performed spe

146 a) hatchling production at seventeen nesting beaches in Bahia, Espirito Santo, and Rio de Janeiro, Br

147 The more tropical nesting beaches in Brazil, such as those in Bahia, are projected

148 Study of multiple beaches in different geographic settings provided new in

149 Waterborne pathogens were measured at three beaches in Lake Michigan, environmental factors for pred

150 ll storm drains on FIB pollution at enclosed beaches in Newport Bay, the second largest tidal embayme

151 swimming and wading in marine and freshwater beaches in six U.S. states, and CHEERS, which evaluated

152 robial communities at four freshwater public beaches in southern Ontario, Canada and analysed communi

153 of samples collected at three Lake Michigan beaches in summer, 2010.

154 n 2010, and other oiled samples collected on beaches in the northern Gulf of Mexico from July 2010 un

155 cific (SE) DNA sequence at seven Great Lakes beaches, in algae, water, and sediment.

156 Higher waves associated with dissipative beaches increase the disturbance of strand species, whic

157 ring of the eight kill localities at Wally's Beach indicates these animals were killed over a short p

158 hiking" passenger organisms, on an Antarctic beach inside the flooded caldera of an active volcanic i

159 MDL) implementation at a southern California beach involved ultraviolet treatment of watershed draina

160 been made that the wrack accumulating on the beach is a major source of FIB to the surf zone.

161 rce tracking methods indicate the FIB at the beach is of human and bird origin.

162 ling confirmed that the source of FIB to the beach is terrestrial rather than marine.

163 t urban waterways, lakes, and coastal marine beaches is responsible for costs that should be accounte

164 on, cost efficiency, and collaboration among beach jurisdictions.

165 ry of non-native kelp washed up on Antarctic beaches led us to question the permeability of these bar

166 Main Hawaiian Islands (sea surface, windward beaches, leeward beaches, and seafloor) to better descri

167 areas where magnetic signatures of adjacent beach locations converged over time, whereas nesting den

168 Shoreline hardening, which causes beach loss globally, will accelerate with sea level rise

169 rate with sea level rise (SLR), causing more beach loss if management practices are not changed.

170 Maximum risk of shoreline hardening and beach loss is projected to occur from modern-day and nea

171 odels of beach water quality may help reduce beach management errors and enhance protection of public

172 Traditional beach management that uses concentrations of cultivatabl

173 The monitoring approach selected by beach managers may be a combination of available tools t

174 On highly impacted beaches, microplastic concentrations (<1mm) can reach 3%

175 itats to remain suitable for nesting through beach migration.

176 ater (n = 4), were collected in Wrightsville Beach, NC.

177 future shoreline hardening patterns on sandy beaches need deeper analysis.

178 t that upon receiving a partial memory cue ('beach'), neurons in the hippocampus coordinate reinstate

179 were tested using data collected for Tairua beach, New Zealand with 18 years of daily averaged along

180 marine aerosol at Sant Andreu de Llavaneres beach (northwestern Mediterranean Sea).

181 A beach nourishment with approximately 1/3 fine-grained se

182 um to compare to a tar ball collected on the beach of Louisiana.

183 ng along the tidal gradient of the North Sea beach of the Dutch barrier island Schiermonnikoog was an

184 sources, we collected 12 TB samples from the beaches of Gujarat (Tithal, Maroli, Umbergam, and Nargol

185 c drowning event occurred along southeastern beaches of Lake Michigan on a sunny and calm July 4, 200

186 rge numbers of SOAs were buried in the sandy beaches of the northeastern Gulf of Mexico.

187 how dramatic this increase is likely to be: beached oil has an environmental residence of years, whe

188 paper presents data collected at a fine sand beach on Lake Huron, Canada over three field events.

189 erved 1-2 m below the shoreline at two sandy beaches on Lake Erie, Ontario, Canada.

190 s a proxy for risk of hardening at all sandy beaches on the island of O'ahu, Hawai 'i.

191 consisting of a screen background image of a beach or mountains, accompanied by corresponding sounds.

192 4 October 2019 at Salishan Lodge in Gleneden Beach, Oregon.

193 Our goal was to identify nesting beach origins for turtles foraging here.

194 of females congregating at a single nesting beach over a few days to oviposit their eggs.

195 e quality of the available information about beach plastic debris worldwide to highlight where the mo

196 d inorganic nitrogen (DIN) concentrations in beach pore water along the Santa Barbara, California coa

197 We coupled measurements of beach pore water residence time, determined using the ra

198 rida, burying oil up to 70 cm depth in sandy beaches, posing a potential threat to environmental and

199 ersers from a different habitat (nearby lake beaches) produced half as many offspring.

200 We recruited beachgoers at Boqueron Beach, Puerto Rico, during the summer of 2009.

201 study participants who recreated at Boqueron Beach, Puerto Rico.

202 The age of the postglacial raised beaches ranges from 10.7 cal.

203 prove public health protection at California beaches relative to current practices.

204 so found that heterogeneity greatly affected beach response.

205 rize the magnetic coordinates of their natal beach, returning to that combination of parameters to la

206 Conservative estimates for a Mediterranean beach reveal that tourism activities during a summer day

207 n of demography, economy, and El Nino-driven beach-ridge formation on the Chira beach-ridge plain of

208 no-driven beach-ridge formation on the Chira beach-ridge plain of Northwestern Peru has changed the n

209 ns and entombed within coatings of dripstone beach-rock silica cement.

210 y averaged alongshore shoreline position and beach rotation (orientation) data obtained from a camera

211 able spatially and temporally along the nine beaches sampled in Central California.

212 differential decay of wastewater bacteria in beach sand and in seawater provides a kinetic explanatio

213 Elevated fecal indicator bacteria (FIB) in beach sand and pore water represent an important nonpoin

214 was contrasted by the increase in indigenous beach sand and seawater microbiota, and the overall micr

215 a and the change of microbial communities in beach sand and seawater.

216 The dry and nutrient-poor beach sand presents a taxing environment for microbial g

217 ition of golf-ball-size DWH-SOAs embedded in beach sand takes at least 32 years, while SOA degradatio

218 showed significantly smaller decay rates in beach sand than in seawater.

219 wer decrease of total bacterial densities in beach sand than in seawater.

220 in transporting microbial contaminants from beach sand to coastal water is unknown.

221 suspended in seawater through medium-grained beach sand under transient and saturated flow conditions

222 on three different types of floor surfaces: beach sand, a paved street or grass.

223 e often-observed higher abundance of FIBs in beach sand, and the NGS-based microbial community analys

224 radation in the tidally ventilated permeable beach sand, emphasizing the role of the sandy beach as a

225 venger-assisted magnesiothermic reduction of beach sand.

226 r enhancing oil spill remediation efforts in beach sands and coastal sediments and underscore the rol

227 Foreshore beach sands and pore water may act as a reservoir and no

228 The results reveal that SOAs buried deep in beach sands can be decomposed through relatively rapid a

229 o cENT through laboratory columns containing beach sands.

230 d, groundwater, and beach sites, including a beach scour pond and tidal creek.

231 mapA abundance in water was correlated with beach seasonal mean log10 E. coli concentration.

232 Beach seasonal mean mapA abundance in water was correlat

233 Beach sediment and sand are recognized as nonpoint fecal

234 Oiled beach sediment, tar ball, and marsh samples were collect

235 order, from fastest to slowest: high energy beach sediments > low energy beach sediments > marsh > t

236 st: high energy beach sediments > low energy beach sediments > marsh > tar balls.

237 Our results indicate that beach sediments at the sediment-water interface could se

238 weak but significant differentiation amongst beaches separated by only a few kilometres on the island

239 camel in North America occurs at the Wally's Beach site, Canada.

240 s collected from watershed, groundwater, and beach sites, including a beach scour pond and tidal cree

241 ltration velocity (i.e., beaches with higher beach slope and wave height, and lower terrestrial groun

242 ach, the Cape Hatteras Tropical Limit/Myrtle Beach South Carolina, and Florida Keys/Ten Thousand Isla

243 The stream- and beach-spawning ecotypes exhibited striking morphological

244 which suggests a stochastic dynamics behind beach stabilization.

245 n blubber collected from fishery bycatch and beach-stranded specimens for 40 females of known reprodu

246 Lakes beaches comes largely from individual beach studies.

247 At one beach, stx2 gene abundance was positively correlated wit

248 endent sex determination and obligate use of beaches subject to sea level rise (SLR).

249 d bird-associated Catellicoccus, through the beach subsurface.

250 production, while the more temperate nesting beaches, such as those in Rio de Janeiro, are projected

251 re flow speeds increase compared to a planar beach, suggesting the need to include a buffer zone behi

252 independent of the population at the landing beaches, suggesting that all categories of fish landing

253 E. coli distribution at a coarse sand-cobble beach suggests that interstitial pore water flow and dis

254 h your photo album and seeing a picture of a beach sunset brings back fond memories of a tasty cockta

255 Beach surface water and groundwater collected in Sendai

256 in the sediment were similar to those at the beach surface.

257 We found that the response of the beach system was characterized by fluctuations of embedd

258 model FIB dynamics in the coupled watershed-beach system.

259 nd limits of the model; Jupiter Florida/Vero Beach, the Cape Hatteras Tropical Limit/Myrtle Beach Sou

260 ris pieces (n = 4671) were collected from 11 beaches, three sea surface tows, and three seafloor dive

261 ate a digital elevation model of the nesting beach to estimate impacts of projected SLR.

262 se spatial proximity, yet dispersal from the beach to the streams was more common than dispersal betw

263 d seawater, and resin pellets sampled on the beach, to investigate the origin and uniqueness of plast

264 Being able to accurately model beach topography using digital terrain models (DTMs) is

265 planation for the empirical relation between beach type and foredune size, in which large (small) for

266 ere is insufficient clinical evidence that a beach umbrella alone can provide adequate sun protection

267 A beach umbrella alone may not provide sufficient protecti

268 ure sunburn protection offered by a standard beach umbrella compared with that provided by sunscreen

269 The shade provided by a beach umbrella or protection provided by sunscreen with

270 andomly assigned to 2 groups: 1 using only a beach umbrella, and the other using only sunscreen with

271 et for 83 foraging turtles traced to nesting beaches using flipper tags and/or PIT tags (n = 72), or

272 onitoring outcomes expected at Lake Michigan beaches using protocols for indicator bacteria including

273 e of Health, Memphis VA Medical Center, Long Beach VA Healthcare System, Department of Veterans Affai

274 Saliva was collected on the day of the beach visit (S1); after 10-14 days (S2); and after 30-40

275 of debris (up to 4,496.9 pieces/m(2)) on the beach was buried <10 cm in the sediment.

276 ches, we tested enrichment cultures from 273 beach water and 22 tributary samples for EC, ENT, and ge

277 ng the migration and exchange of FIB between beach water column and sediment is desired to better pre

278 s have a disproportionate impact on enclosed beach water quality for five reasons: (1) dry weather su

279 system may be the best option for improving beach water quality in Newport Bay and other urban-impac

280 thogen gene quantification may be useful for beach water quality management.

281 Predictive, nowcast models of beach water quality may help reduce beach management err

282 gement and can be used to develop predictive beach water quality models.

283 l abatement BMP was associated with improved beach water quality, and this appears to be the first re

284 re did not provide sufficient improvement of beach water quality, prompting further assessment.

285 all/flow related dominating factor affecting beach water quality, while beaches having a deterioratin

286 The PH-BEACH-WD40 (PBW) protein family members play a role in c

287 Using 12 representative beaches, we tested enrichment cultures from 273 beach wa

288 to examine the efficacy of the Atkins, South Beach, Weight Watchers (WW), and Zone diets, with a part

289 with salinity close to seawater, pumped from beach wells in coastal aquifers which penetrate beneath

290 Sea surface and windward beaches were dominated by severely weathered, less dense

291 tributary fjord to Wahlenbergfjorden, raised beaches were surveyed and organic material collected to

292 onbuoyant discharge at an alongshore uniform beach with constant slope using a wave-resolving hydrody

293 Beaches with good performing models usually have a rainf

294 te and vertical infiltration velocity (i.e., beaches with higher beach slope and wave height, and low

295 Beaches with higher wave-induced infiltration rate and v

296 ethod results were generally high, except at beaches with historically high concentrations of EC.

297 milling in the swash zone and abrasion when beached, with wind transport leading to the temporary bu

298 rom the whale are also found occasionally on beaches worldwide.

299 study investigates one nonfecal FIB source, beach wrack (decaying aquatic plants), and its impacts o

300 erature loggers were buried at depths and in beach zones representative of turtle nesting sites.