ライフサイエンスコーパス: bleach

1 or cnidarian symbiosis and dysbiosis (i.e., "bleaching").

2 on density (e.g., use of chlorine-containing bleach).

3 tion of an amine under oxidative conditions (bleach).

4 ction and the loss of algal symbionts (coral bleaching).

5 te-driven disturbances (hurricanes and coral bleaching).

6 orization (namely degumming, neutralization, bleaching).

7 protection to prevent their deactivation by bleach.

8 visual pigment in our photoreceptor cells is bleached.

9 st conditions can lead to thermal stress and bleaching.

10 ess, before reaching temperatures that cause bleaching.

11 sistently immobile for more than 2 min after bleaching.

12 ecline due to mortality by heat-driven coral bleaching.

13 three stages: neutralization, degumming, and bleaching.

14 he breakdown of this symbiosis, termed coral bleaching.

15 lerant symbionts can also sometimes mitigate bleaching.

16 vity of rod photoresponses following pigment bleaching.

17 scleractinian corals for signs of disease or bleaching.

18 signal, and eventually to its loss by photo-bleaching.

19 rwise induce cellular damage and chlorophyll bleaching.

20 king and oxygen scavenging systems to reduce bleaching.

21 r the development of visual symptoms such as bleaching.

22 ive and possibly acclimatize to annual coral bleaching.

23 ing and cell death, and finally induce coral bleaching.

24 cation and climate change impacts like coral bleaching.

25 a from the effects of both acidification and bleaching.

26 asing levels of both coral disease and coral bleaching.

27 green, a process referred to as chlorosis or bleaching.

28 nt photocurrent following equivalent pigment bleaching.

29 e of rod phototransduction following pigment bleaching.

30 evidence of intraband-controlled absorption bleaching.

31 dly exposed to the maxima, which exacerbates bleaching.

32 eaching and hypochlorite-induced fluorescein bleaching.

33 ociated with hydrogen and carbamide peroxide bleaching.

34 al activity of commonly used antiseptics was bleach (1:10) > cavicide (1:10) > ethanol (70%).

35 Bayesian blinking and bleaching (3B) reconstruction reveals that the distance

36 umination with a femtosecond-pulsed laser to bleach a nucleic acid-binding dye causing dose-dependent

37 tter the oil quality obtained because of the bleaching ability of adsorbents.

38 Thus, bleaching adaptation renders mouse rods responsive to mo

39 that phototransduction gain adjustments and bleaching adaptation underlie rod recovery.

40 n, elevated nutrient loading increased coral bleaching; Agaricia spp. of corals exposed to nutrients

41 itive without hindering the diffusion of the bleaching agent and if the spheres could be used as a ca

42 ral reefs in the region, and the coral reef "Bleaching Alert" alarm was not raised.

43 Differential bleaching among corals was widely variable (mean taxon-B

44 Here, by using polarized light to bleach and probe an internal YFP-FliN fusion, we show th

45 able to dark-adapt in the retina following a bleach and to use exogenous 9-cis retinol for pigment re

46 ays; RR 0.85, 95% CI 0.69-1.04; p=0.116), or bleach and UV (n=131; 45.6 cases per 10 000 exposure day

47 p, 5438 in the bleach group, and 5863 in the bleach and UV group.

48 V-C] light except for C difficile, for which bleach and UV-C were used); bleach; and bleach and UV-C.

49 hich bleach and UV-C were used); bleach; and bleach and UV-C.

50 esters and glycidyl esters (GEs) of refined, bleached and deodorized (RBD) palm olein during deep-fat

51 RBD (Refined, Bleached and Deodorized) canola oil and vitamin E acetat

52 Phage consortia differed between bleached and diseased tissues.

53 plied 3 months later, corals that previously bleached and were now dominated by D1a Symbiodinium expe

54 da and P. daedalea declined from 2011 due to bleaching and black-band disease.

55 hile corals can recover from single isolated bleaching and can acclimate to recurring bleaching event

56 g sponges depended on the intensity of coral bleaching and consequent coral mortality.

57 eralizing agent could increase the safety of bleaching and decrease the severity of its side effects.

58 Coral bleaching and disease outbreaks are often inter-related

59 rogen cycling may be tightly linked to coral bleaching and disease.

60 Measurements of bleaching and dissociation kinetics at the cell cortex r

61 Biofilm growth was confirmed by bleaching and flushing the wells and observing the NMR s

62 o elevated temperatures that can cause coral bleaching and high levels of mortality of corals and ass

63 hydrorhodamine 123, AAPH-induced fluorescein bleaching and hypochlorite-induced fluorescein bleaching

64 The event caused coral bleaching and massive mortality of corals and other reef

65 cause photochemical reactions that result in bleaching and mineralization of tDOM.

66 caused by global warming that induced coral bleaching and mortality events globally.

67 s seawater temperatures and consequent coral bleaching and mortality influence these shifts.

68 Taxon-specific bleaching and mortality records (2036) of 374 coral taxa

69 Corals are affected by warming-induced bleaching and postmortem dissolution, but the finding he

70 Thus, annual coral bleaching and recovery could contribute to the selective

71 We conducted repeat bleaching and recovery experiments on the coral Montastr

72 sual pigment, and used it to measure pigment bleaching and regeneration in living mice.

73 Mortality was driven by diseases in 2009, bleaching and subsequent diseases in 2010/2011/2012.

74 downingi severely declined from 2010 due to bleaching and subsequent white syndromes, while D. palli

75 pproach using laser irradiation coupled with bleaching and surface removal was most efficient in elim

76 he Arg66 side-chain conformation affects the bleaching and the on-to-off transition quantum yields, a

77 Ethanol, 70% isopropyl alcohol, dilute bleach, and mechanical cleaning all lack the ability to

78 control corals that had not been previously bleached, and were therefore still dominated by Symbiodi

79 phototoxicity, (iv) blinking, (v) permanent bleaching, and (vi) formation of long-lived intermediate

80 degumming, neutralization, washing, drying, bleaching, and deodorization; deodorization was conducte

81 ross Canada, representing the major pulping, bleaching, and effluent treatment technologies.

82 fer from repeated impacts of cyclones, coral bleaching, and outbreaks of the coral-eating crown-of-th

83 ble D1a symbionts became dominant only after bleaching, and were critical to corals' resilience after

84 icile, for which bleach and UV-C were used); bleach; and bleach and UV-C.

85 ions, 90% are projected to experience severe bleaching annually by 2055.

86 Highly relevant for pulp bleaching are the findings on intermediates of the react

87 It minimizes fluorophore bleaching as well as phototoxic effects and provides a t

88 recommend VR, which rarely requires specimen bleaching, as the standard substrate for immunohistochem

89 ial variation in the timing of annual severe bleaching (ASB) conditions; a point at which reefs are c

90 y locations where the onset of annual severe bleaching (ASB) varies 10 or more years within a single

91 The crocin bleaching assay (CBA) is a common method for evaluating

92 for raw garlic samples, while beta-carotene bleaching assay yielded the highest activity for stir-fr

93 ounds tested by DPPH, FRAP and beta-carotene bleaching assays showed that allicin had an antiradical

94 dical scavenging activity, and beta-carotene bleaching assays.

95 the free radical activity and beta-carotene bleaching assays.

96 H radical scavenging, FRAP and beta-carotene bleaching assays.

97 sion, which can arise from the instantaneous bleaching assumption.

98 g the recommendations for the use of diluted bleach baths, vitamin D, and environmental modifications

99 esters was investigated using beta-carotene bleaching (BCB) and free radical scavenging method DPPH

100 perature microclimates are more resistant to bleaching because of both acclimation and fixed effects,

101 If bleaching becomes an annual event later in this century,

102 stress-sensitive symbionts (Symbiodinium C3) bleached, but recovered (at either 24 degrees C or 29 de

103 f Orbicella faveolata did not prevent repeat bleaching, but may have facilitated rapid recovery.

104 HPLC analyses demonstrate that 11-REs are bleached by bright light and regenerated in the dark.

105 oral cell mortality and symbiont loss during bleaching by over 50%.

106 nstrate for the first time that annual coral bleaching can dramatically alter thermal tolerance in Ca

107 Resultant coral bleaching caused an average 75% reduction in coral cover

108 This method was used without imaging the bleached cell.

109 total internal reflection (TIR) selectively bleaches cerulean-labeled protein proximal to the glass

110 continuous quenching over time attributed to bleaching chlorine-based species.

111 n in the IPM, and it promotes the removal of bleached chromophores and recycling in the nearby retina

112 Exposing these corals to thermal bleaching conditions changes the microbiome for heat-sen

113 re, projections of the onset of annual coral bleaching conditions in the Caribbean under Representati

114 time to adapt and acclimate prior to severe bleaching conditions occurring annually.

115 re increasing the global prevalence of coral bleaching, coral diseases, and coral-mortality events.

116 mmunities also differed between diseased and bleached corals.

117 as the algal colonization and overgrowth of bleaching corals, as well as coral polyp behaviour and i

118 uence the diffusion in the samples, but that bleach correction and fitting introduce large uncertaint

119 cular the high bleach intensity in FRAP, the bleach corrections, and the fitting procedures in the tw

120 icient in each pixel of an image, and proper bleaching corrections, it is now possible to measure the

121 0 years suggested successive events of coral bleaching could shift algae-coral dominated reefs into a

122 Bleaches decrease sensitivity in part by loss of quantum

123 The temperature threshold for coral bleaching depends on the acclimation and adaptation of c

124 time corals in the northern Red Sea did not bleach despite high thermal stress (i.e. DHWs >8 degrees

125 he northern Red Sea has not experienced mass bleaching despite intensive Degree Heating Weeks (DHW) o

126 regions where there are few records of coral bleaching despite the presence of significant heat stres

127 luded that after sodium hypochlorite (dilute bleach) disinfection, the virus was undetectable, but on

128 Here we investigate responses to acute bleaching disturbances on turbid reefs off Singapore, at

129 merical simulations, which take into account bleach duration, granule diameter, and the limited numbe

130 st, or during bleaching, when acid-activated bleaching earth acts as the catalyst.

131 et molecule of the pulp and paper industry's bleaching efforts.

132 odinium D1a), which were not detected before bleaching (either due to absence or extreme low abundanc

133 nclude molecular-motor stepping, fluorophore bleaching, electrophysiology, particle and cell tracking

134 used dilute oxalic acid to pretreat a kraft bleached Eucalyptus pulp (BEP) fibers to facilitate mech

135 k directly followed a high temperature coral-bleaching event and affected at least 13 coral species.

136 ETP coral populations decimated by the 1998 bleaching event can only have recovered from eastern Pac

137 The 2014-2016 global coral bleaching event has sharpened the focus on such interven

138 le and St. Croix reefs after a regional mass bleaching event in 2005.

139 ral holobiont response to an isolated single bleaching event is not an accurate predictor of its resp

140 rld's oceans are in the midst of the longest bleaching event on record (from 2014 to at least 2016).

141 f responses to a major climate-induced coral bleaching event that caused unprecedented region-wide mo

142 ts of superoxide produced by corals during a bleaching event, we show substantial species-specific va

143 tions and shocks such as the 2016 mass coral-bleaching event.

144 concurrent white plague disease outbreak and bleaching event.

145 curately predicted ecosystem response to the bleaching event.

146 f this decline is attributable to mass coral bleaching events and disease outbreaks, both of which ar

147 As coral bleaching events become more frequent and intense, our a

148 Mass coral bleaching events caused by elevated seawater temperature

149 how and why the severity of recurrent major bleaching events has varied at multiple scales, using ae

150 Here we show that bleaching events of the past three decades have been mit

151 onditions under which reefs bounce back from bleaching events or shift from coral to algal dominance

152 ted bleaching and can acclimate to recurring bleaching events that are separated by multiple years, i

153 mperatures are driving increasingly frequent bleaching events that can lead to the loss of both coral

154 Coral bleaching events threaten the sustainability of the Grea

155 though this may be due to under-reporting of bleaching events, it may also be due to physical factors

156 e heatwaves has caused widespread mass coral bleaching events, threatening the integrity and function

157 onse of coral-excavating sponges after coral bleaching events.

158 biont that flourishes in coral tissues after bleaching events.

159 Fluorescence recovery after photo-bleaching experiments showed that Rab5 and Rab4 are recr

160 d-mediated sensitivity to recover from photo-bleach exposure, correlated with lower RPE-drusen comple

161 We show that an additional bleach feature at approximately 510 nm appears when PbI2

162 DA) incorporates a digital camera, a retinal bleaching flash, and a Ganzfeld light source inside a pa

163 hat turbidity will mitigate high temperature bleaching for 9% of shallow reef habitat (to 30 m depth)

164 2D random walk) starting with the first post-bleach frame of the actual data.

165 ated using fluorescence recovery after photo-bleaching (FRAP) and a p53 reporter assay.

166 to nutrients suffered a 3.5-fold increase in bleaching frequency relative to control corals, providin

167 ery trajectories, and predicted increases in bleaching frequency, we predict a prolonged period of su

168 g as an additive to minimize side effects in bleaching gel formulation.

169 alue of diffusion coefficients for arbitrary bleaching geometries, including exaggeratedly large ones

170 tion of diffusion coefficients regardless of bleaching geometry used in the FRAP experiment.

171 ng diffusion coefficients from a rectangular bleaching geometry, created in a confocal image, was lat

172 nce group, 5178 in the UV group, 5438 in the bleach group, and 5863 in the bleach and UV group.

173 hase, electric field-induced colouration and bleaching have a switching time of seconds.

174 vations on weed growth and were developed as bleaching herbicides.

175 ave the materials to complete treatment with bleach in their household.

176 Skin colour was bleached in red peppers exposed to ozone at 2mumolmol(-1

177 s and cones adapt to background light and to bleaches in a manner almost identical to other vertebrat

178 Similarly, past exposure to bleaching in 1998 and 2002 did not lessen the severity o

179 sure had minimal effect on the unprecedented bleaching in 2016, suggesting that local protection of r

180 1998 and 2002 did not lessen the severity of bleaching in 2016.

181 leads to the formation of a pink coloration bleaching in a few milliseconds, in the absence of light

182 cones, but immunohistochemistry and partial bleaching in conjunction with single-cell recording reve

183 propose that the end product of chromophore bleaching in rod photoreceptors, all-trans retinol, is p

184 th disease prevalence and severity and coral bleaching in scleractinian corals, the major habitat-for

185 FIELD, a strategy for fundamentally reducing bleaching in STED/RESOLFT nanoscopy through restricting

186 rnal dialysis of Cs(+) , which increased the bleach-induced desensitization of the photovoltage and s

187 pothesized link between nutrient loading and bleaching-induced coral declines.

188 ngle photons, to detect mutation-induced, or bleaching-induced, local defects or modifications of the

189 e oxidation (62.41 +/- 0.43%), beta-carotene bleaching inhibition (91.75 +/- 0.22%) and Cu(2+)-chelat

190 578 mg/mL), reducing power and beta-carotene bleaching inhibition activities, and also a strong ABTS

191 Overall, we find that the FRAP bleach intensity does not measurably influence the diffu

192 ological differences, in particular the high bleach intensity in FRAP, the bleach corrections, and th

193 e response following moderate visual pigment bleach is delayed in KI/KI mice.

194 average year for the onset of annual severe bleaching is 2040-2043 for all projections.

195 Climate-induced coral bleaching is among the greatest current threats to coral

196 Increasingly frequent severe coral bleaching is among the greatest threats to coral reefs p

197 Severe annual bleaching is projected to start 10-15 years later at hig

198 ocusing followed by Western blot analysis of bleached isolated retinae showed little dephosphorylatio

199 easurements depended critically on the exact bleaching kinetics and was correctly quantified by the C

200 In this sense, the behavior of a bleached kraft hardwood pulp when recycled was investiga

201 The frequency of bleaching-level thermal stress increased three-fold betw

202 photoresponses following exposure to bright bleaching light.

203 lecule activation (increased background) and bleaching (loss of detections).

204 high-latitude reefs of later onset of annual bleaching may be negated by the effects of acidification

205 nt of FRAP (fluorescent recovery after photo-bleaching) modified to interrogate the diffusion path-le

206 ary outcome was not statistically lower with bleach (n=101; 41.6 cases per 10 000 exposure days; RR 0

207 not changed after adding UV to cleaning with bleach (n=38 vs 36; 30.4 cases vs 31.6 cases per 10 000

208 ght intensities and adapt to backgrounds and bleaches nearly identically.

209 volumetric analysis of oxidizing agents and bleach neutralization during water treatment.

210 The vast majority of bleaching observations to date have been associated with

211 After excitation we observe a bleach of all involved bases.

212 QD under equilibrium conditions, including a bleach of the first exciton transition and the appearanc

213 ide-alkyne cycloaddition, and the controlled bleaching of fluorescent probes conjugated to azide- or

214 cooling, during which state filling induced bleaching of interband and exciton transitions curiously

215 After complete bleaching of rhodopsin, the ERP recovered in two phases.

216 The bleaching of the color could be clearly observed by the

217 ent electrolyte, and the onset potential for bleaching of the FA-PVSK absorbance is used to estimate

218 posure of the cell to the laser and eventual bleaching of the sample.

219 KEY POINTS: Following substantial bleaching of the visual pigment, the desensitization of

220 nterestingly, these polymers actually show a bleaching of their neutral absorptions in the near-infra

221 Bleaching of vital teeth has become common practice in c

222 Sodium hypochlorite (dilute bleach) offers effective disinfection against adenovirus

223 high primary oxidation stability, while the bleached oil had a low incidence of secondary oxidation.

224 stinctive geographic footprints of recurrent bleaching on the Great Barrier Reef in 1998, 2002 and 20

225 on the localization precision in some other bleaching- or blinking-assisted techniques.

226 e conditions of industrial hydrogen peroxide bleaching (P stage).

227 ria applied in the global effort to document bleaching patterns creates challenges for the developmen

228 Artificial overexpression of PsrR1 led to a bleaching phenotype under moderate light growth conditio

229 in diseased or healthy tissues compared with bleached portions of diseased tissues.

230 ng for this connectivity may be important in bleaching predictions.

231 The coloration and bleaching process in the ECD component show good cyclic

232 within the 300 nm granule diffused into the bleached proximal regions.

233 that NPY-cer equilibrated within the 300 ms bleach pulse, and therefore had a greater mobility than

234 Mass coral bleaching quickly ensued, killing 40% of the resident co

235 ated in terms of beta-carotene/linoleic acid bleaching, radical scavenging, reduction of metal ions a

236 ging, reported to reduce fluorescent protein bleaching rates, thereby increasing the precision of sup

237 This bleach recommendation is internally inconsistent, a rela

238 a unique compilation of corresponding coral bleaching records from throughout the region.

239 Based on past bleaching recovery trajectories, and predicted increases

240 inol produced robust sensitivity recovery in bleached red and blue cones but not in red and green rod

241 A bleaching reduction by up to 100-fold is demonstrated.

242 The bleaching reduction can be converted into accordingly br

243 Without considering bleaching, reef growth will likely decline on most reefs

244 buffered from thermal stress and will avoid bleaching-related mass mortalities caused by increasing

245 e needed studies relating thermal history to bleaching resistance and community composition.

246 nt tissue area affected and a taxon-specific bleaching response index (taxon-BRI) was calculated by a

247 nd validate a novel framework to standardize bleaching response records and estimate their measuremen

248 ithin a given site and event (60% and 40% of bleaching response variance of all records explained, re

249 indicate that increased thermotolerance post-bleaching resulted from symbiont community composition c

250 communities shifted substantially following bleaching, returning towards pre-disturbance structure o

251 of the pump-probe spectra where photoinduced bleaching rises abruptly 20 fs after photoexcitation.

252 Only live bacteria are revealed since bleached samples are not labeled.

253 energetic blue shift observed for transient bleach signals results from rapid hot electron relaxatio

254 wavelength as cyanine 5, Cy5) were found to bleach significantly less than FAM and Cy5; i.e., the fi

255 r lignin-free model biomass samples--Avicel, bleached softwood, and bacterial cellulose--to find corr

256 Silver ink was printed and chlorinated with bleach solution.

257 Finally, Glc-bleached SSB01 cells appeared unable to efficiently popu

258 ndent of light, algal symbiont abundance and bleaching status, but depend on coral species and bacter

259 The isobaric forms occur only during the bleaching step of the refining process and remain unalte

260 hemical analysis, we find that the number of bleaching steps in SMSr-GFP-positive spots displays a su

261 n detection in live bacteria without initial bleaching steps.

262 cells with curcumin increased the number of bleaching steps.

263 s of each species from a single histogram of bleaching steps.

264 ry that subjects corals to a protective, sub-bleaching stress, before reaching temperatures that caus

265 y: the partnership is highly susceptible to 'bleaching' (stress-induced symbiosis breakdown), but str

266 ogy and direct semi-quantitative analysis of bleaching suggests the existence of two membrane-bound D

267 ging activity, reducing power, beta carotene bleaching system and TBARS assay) showed that the variet

268 average year for the onset of annual severe bleaching that is ~20 years later (2062 vs. 2044).

269 ONOO(-) can readily bleach the chromophore and thus recover the luminescence

270 We find that to bleach the first exciton transition by an average of 1 c

271 ased susceptibility in Porites astreoides to bleaching the following year.

272 not an accurate predictor of its response to bleaching the following year.

273 y contribute to pathogen resistance but also bleaching, the loss of essential algal symbionts.

274 es triggered a pan-tropical episode of coral bleaching, the third global-scale event since mass bleac

275 between 2006 and the onset of annual severe bleaching (thermal stress >8 degree heating weeks); a po

276 bean are not refugia because they have lower bleaching threshold temperatures than shallow reefs.

277 s, mesophotic reef bleaching was driven by a bleaching threshold that declines 0.26 degrees C every +

278 f-building corals that live well below their bleaching thresholds and thus we propose that the region

279 received limited attention despite differing bleaching thresholds for summer and winter.

280 scribe an oxidative strategy using household bleach to release all types of free reducing N-glycans a

281 was comparable with, or more effective than, bleach treatment against established biofilms of S. ente

282 r characteristics of HA-AAs before and after bleaching treatment, we found that only HA, synthesized

283 d performance of HA-AAAs were observed after bleaching treatment.

284 e effective than electrolyzed reduced water, bleach, VegWash and DI water on pesticide removal.

285 Bleached visual pigment produced an acceleration of the

286 day progressed, which was ascribed to photo bleaching/volatilization of BrC and/or due to rising bou

287 In this study, bleach was added in three different dosages to six water

288 sinfectant except for C difficile, for which bleach was used); UV (quaternary ammonium disinfectant a

289 r two thermal stress events, mesophotic reef bleaching was driven by a bleaching threshold that decli

290 ing, the third global-scale event since mass bleaching was first documented in the 1980s.

291 Severe bleaching was restricted to the central and southern Red

292 l stress (i.e. DHWs >8 degrees C-weeks), and bleaching was restricted to the central and southern Red

293 The procedure consists of a bleach wash, enzymatic digestion, first fixation, 'crack

294 The almost equal NPY-cer bleaching when probed with TIR and epifluorescence indic

295 se, when H3PO4 acts as a catalyst, or during bleaching, when acid-activated bleaching earth acts as t

296 is observed without loss of the ground-state bleach, which is a clear signature of electron injection

297 r Photobleaching (FRAP) measurements assumes bleaching with a circular laser beam of a Gaussian inten

298 veloped with DAB, with and without overnight bleaching with hydrogen peroxide, 4%.

299 there have only been very few recordings of bleaching within the Red Sea despite covering a latitudi

300 Additional corals that were initially bleached without heat by a herbicide (DCMU, at 24 degree