ライフサイエンスコーパス: ash

1 id-extractable REE content for more than 100 ash samples were correlated with characteristics such as

2 19 mm Pfund), moisture (31 +/- 5.4 g/100g), ash (0.531 +/- 0.632 g/100g), electrical conductivity (1

3 ied coconut haustorium contained 1.05+/-0.2% ash, 44.2+/-4.6% soluble sugar, 24.5+/-3.2% starch, 5.50

4 amylose, 4.84+/-0.29% moisture, 0.88+/-0.21% ash, 1.34+/-0.11% proteins and 92.73+/-0.48% carbohydrat

5 .88%), soluble carbohydrates (17.59-25.37%), ash (22.31-38.55%), minerals (0.96-1.82 for Na/K ratios)

6 moisture, 15.89% protein, 13.72% fat, 3.52% ash, 16.74% dietary fiber and 61% carbohydrates.

7 ude protein, 0.27g lipid, 0.17g fibre, 0.63g ash, 29.69g carbohydrates, 262.30mg potassium, 61.53mg m

8 tained 92.15% protein, 0.31% lipid and 0.72% ash.

9 otein (20%), insoluble dietary fibres (74%), ash (51%), and alpha-linolenic acid (67.4%).

10 ntained 28.7% crude protein, 7.1% fat, 10.9% ashes, 44.4% carbohydrate and 3.0mg 100g(-1) calcium and

11 , were: 72 and 72 (moisture); 0.87 and 0.90 (ashes); 1.5 and 1.4 (proteins); 0.63 and 0.54 (lipids) a

12 d that seeds contained 5.30% moisture, 3.99% ash, 9.19% fat, 14.31% fiber, 27.21% protein and 45.30%

13 ndex resulted into flours with higher a( *), ash content and protein content.

14 ile profile of wines aged in cherry, acacia, ash, chestnut and oak wood barrels was studied by GC-MS,

15 and chips of cherry, chestnut, false acacia, ash and oak wood was studied by LC-DAD-ESI/MS, to identi

16 possessing higher moisture content, acidity, ash and HMF but a lower level of total sugars.

17 escribed, such as sugars, moisture, acidity, ash and electrical conductivity, color, 5-HMF and diasta

18 honey samples (moisture, pH, total acidity, ash, dry matter, and qualitative absence of hydroxymethy

19 nt, electrical conductivity, water activity, ashes content, pH, free acidity, colorimetric coordinate

20 ption of Pavlof Volcano, Alaska, produced an ash plume that caused the cancellation of more than 100

21 de fibre (36.92%), carbohydrate (40.07%) and ash (8.17%) contents.

22 8.0% PGJ had a high fiber (5.60+/-0.13%) and ash (0.76+/-0.02%) contents, TPC (28.32+/-2.10mg GAE/100

23 gredients such as carbohydrates (69.77%) and ash (3.67%).

24 orrespond to the U and Th concentrations and ash contents of their feed coals, and we show that these

25 al products, along with smoke condensate and ash from these samples.

26 cate that both anaerobic metal corrosion and ash hydration/carbonation contribute to landfill tempera

27 oducts was positively correlated with DF and ash contents and their hydration properties.

28 h and lipids increased, while that of DF and ash decreased.

29 the air emissions (NOx, SOx, PAH, etc.) and ash flows.

30 de fiber and energy value with lower fat and ash content as compared to the biscuits obtained from na

31 tions were correlated with nitrogen, fat and ash content of initial materials, while residual mycelia

32 79 seeds and mucilage respectively), fat and ash content.

33 Protein, fat and ash contents were found to be vary significantly (LSD<0.

34 pirable smoke invariably in As(III) form and ash invariably as As(V).

35 5-11.6 g/100 g), lipid (1.0-2.2 g/100 g) and ash (2.2-3.3 g/100 g) varied significantly accordingly t

36 losions release large amounts of hot gas and ash into the atmosphere to form plumes rising several ki

37 itively correlated with nitrogen, lignin and ash, and negatively with hemicelluloses and carbohydrate

38 Arrowhead tubers with protein, lipid and ash content of 4.60%, 2.27% and 6.15%, respectively were

39 The moisture, protein, total lipid, and ash values (g/100g) ranged from 71.13 to 78.39; 18.10 to

40 emical parameters (pH, acidity, moisture and ash contents, antioxidant activity, colour, and texture)

41 t content and acid value; lower moisture and ash; and was softer than the control.

42 direct application in constraining plume and ash dispersal models.

43 Soaking improved protein and ash by 2.10 and 2.48 percent respectively.

44 acidity, total glucose+fructose, protein and ash contents of honey samples ranged from 17.1% to 20.0%

45 Protein and ash proportions were unaltered in any of the treatments.

46 ant macronutrients, followed by proteins and ash.

47 852 protein-coding genes of which 25% appear ash specific when compared with the genomes of ten other

48 t and quantify volcanic ash in an artificial ash cloud created by dispersal of volcanic ash from a se

49 Powder River Basin ashes had the highest extractable REE content, with 70%

50 higher calcium content of Powder River Basin ashes, which enhances their solubility in nitric acid.

51 Recently, a brominated CS with biomass ash as the carbon source (Br-Ash) was developed as an al

52 ral hydrate formation, while WEOM from black ash showed a higher reactivity for haloketone formation

53 of WEOM followed white ash > control > black ash and fluorescence region II (excitation 220-250 nm; e

54 tus (control) and burned detritus with black ash (moderate severity) and white ash (high severity) as

55 ed to the control, WEOM from white and black ashes had lower reactivity in forming trihalomethanes (5

56 Bottom ash exhibited the heaviest Tl isotope composition (epsil

57 equipment (WEEE), plastics, fly ash, bottom ash, and digestate), leachate water, and atmospheric dus

58 luidized bed combustion (FBC) fly and bottom ashes.

59 Pb), with respect to MSW incineration bottom ashes support the potential for reuse of HTAG slag; howe

60 All of the bottom ashes collected in these power plants were isotopically

61 degrees ), proteins, lipids, carbohydrates, ash, Ca, Mg, P and total solids (except in the tofu) and

62 thogen Hymenoscyphus fraxineus, which causes ash dieback disease.

63 the fungus Hymenoscyphus fraxineus, causing ash dieback, and in North America by the herbivorous bee

64 d is also promising for waste glass and coal ash recycling.

65 lina) to evaluate possible leaking from coal ash ponds.

66 Overall, As in coal ash is not environmentally stable and can participate in

67 fingerprints that are characteristic of coal ash at all but one site.

68 Given the large number of coal ash impoundments throughout the United States, the syste

69 The risk of the mobilization of coal ash into the environment has highlighted the need for th

70 the systematic evidence for leaking of coal ash ponds shown in this study highlights potential envir

71 vide strong evidence for the leaking of coal ash ponds to adjacent surface water and shallow groundwa

72 er plants are producing huge amounts of coal ash that may be applied to a variety of secondary uses.

73 ssment of the environmental behavior of coal ash, particularly with respect to toxic trace elements s

74 e 2008 Tennessee Valley Authority (TVA) coal ash spill affected waters; (2) CCR effluents from power

75 ential environmental risks from unlined coal ash ponds.

76 Additionally, H. fraxineus colonises ash debris and grows in soil in the absence of ash tissu

77 nea, is causing a severe mortality of common ash trees (Fraxinus excelsior); this is raising concerns

78 he future spatial distribution of the common ash.

79 DE-209 in fire stations include contaminated ash tracked back from fire events via boots, clothing, a

80 reviously characterized in moisture content, ash and nitrogen.

81 c biodegradation, anaerobic metal corrosion, ash hydration and carbonation, and acid-base neutralizat

82 A de-ashed humic acid (i.e., metals being removed) scavenged

83 rticulate + colloidal-Pu) decreased after de-ashing.

84 ntly, there are no means available to detect ash in flight as the particles are too fine (radii < 30

85 proximal geological record, which dispersed ash up to 8000 km from source.

86 plastics is described, consisting of (1) dry ashing the plastic sample and tracers in low mass crucib

87 The food samples were digested by dry ashing procedure and their minerals were determined by a

88 The use of low mass ULB EF-Cu boats for dry ashing successfully overcame the problem of crucible-gen

89 This study compared the dry ashing and wet digestion methods of processing food samp

90 The dry ashing method is recommended for digestion of food items

91 Samples were alkali dry-ashed, dissolved in water, and iodine assayed by spectro

92 evaluated were relatively higher in the dry-ashed samples than the wet-digested samples.

93 s accidental introduction from Asia, emerald ash borer (EAB), Agrilus planipennis Fairmaire (Coleopte

94 sects, including the newly sequenced emerald ash borer and bull-headed dung beetle.

95 sive forest and urban tree pest, the emerald ash borer (EAB, Agrilus planipennis).

96 erature on host resistance of ash to emerald ash borer (EAB, Agrilus planipennis), an invasive specie

97 In Europe, the emerging ash dieback disease caused by the fungus Hymenoscyphus f

98 The risk of extensive ash clouds to aviation is thus poorly quantified.

99 s to spread, it could functionally extirpate ash with devastating economic and ecological impacts.

100 etected in water content, as well as in fat, ash, protein and carbohydrate content.

101 cterised for moisture content, protein, fat, ash, pH and titratable acidity, mineral content (sodium,

102 etermined chemical parameters (protein, fat, ash, soluble and insoluble fibre) by standard AOAC metho

103 ed: moisture, ether extract, protein, fiber, ash, sugar fraction, starch content, infrared spectrosco

104 on (protein, non-fibre carbohydrates, fibre, ash and total polyphenolics) and amino acid profiles.

105 cid, polyphenol, proteins, fat, crude fibre, ash and carotenoids content, and antioxidant activity.

106 mall island in pyroclastic deposits and fine ash; since then, microbes, plants and birds have begun t

107 Attrition elevates fine ash production which, in turn, has consequences for erup

108 tes to the anomalously rapid fallout of fine ash and occurrence of concentrically layered aggregates

109 Our experimental results indicate that fine ash production and surface area generation is fast (<15

110 aggregation of approximately 95% of the fine ash and stripped much of the erupted mass out of the atm

111 The cloud was composed of very fine ash (mean radii ~10 mum) collected from Iceland immediat

112 d combustion borne particulates, such as fly ash.

113 lon(205)Tl approximately 0), followed by fly ash (epsilon(205)Tl between -2.5 and -2.8) and volatile

114 Here, spheroidal carbonaceous fly ash particles (SCPs), byproducts of industrial fossil-fu

115 Coal fly ash (CFA) is a by-product of coal combustion that can af

116 Coal fly ash (CFA) is a byproduct of coal combustion and is a sou

117 be uniquely responsive to insoluble coal fly ash compared with the prototypical soluble agonist capsa

118 her gallium sources such as zinc or coal fly ash may be required.

119 585V variant was less responsive to coal fly ash particles due to reduced translation of protein and

120 Overall, this study shows that coal fly ash production could provide a substantial domestic supp

121 Here, we examined As speciation in coal fly ash samples and transformations in response to aquatic r

122 Feeding Hg-loaded coal fly ash to the cement kiln introduces additional Hg into the

123 ells, IL-8 secretion in response to coal fly ash treatment was reduced for cells heterozygous for TRP

124 owever, the typical REE contents in coal fly ash, particularly in the United States, have not been co

125 tion state in gasoline, diesel, and coal fly ash, while biomass burning contained a combination of Se

126 re more responsive to capsaicin and coal fly ash.

127 reclamation of REEs from coal combustion fly ash has been proposed as a way to supplement REE mining.

128 types of coal feedstocks that determine fly ash composition.

129 Class F fly ash may act as an excellent scrubber and fixation reagen

130 r contributors to the total REE value in fly ash, based on their contents and recent market prices.

131 ntrations varied from below 0.002 mg/kg (fly ash) to 188 +/- 125 mg/kg (plastics).

132 he generation of PCDD/Fs on particles of fly ash, even in the absence of transition metals.

133 d electronic equipment (WEEE), plastics, fly ash, bottom ash, and digestate), leachate water, and atm

134 The signatures in the fly ash can be accounted for using a simple unidirectional f

135 The fly ash in all of these power plants was, in contrast, enric

136 When the fly ash particle became airborne, the effective density depe

137 wed calculation of the percentage of the fly ash particles below 100 nm.

138 ay constitute a considerable part of the fly ash particles below 100 nm.

139 The fly ash samples were fractionated at 2 mum, yielding fine fr

140 evaluates the potential of using Class F fly ashes (<20% CaO), in combination with excessive fines fr

141 ion generated nanoparticles are found in fly ashes but that many ENO finally end up in this matrix.

142 Analysis of some waste incinerator fly ashes revealed a significant difference between their EP

143 ation of the nanoparticulate fraction of fly ashes is therefore needed.

144 Electron microscopic images of fly ashes showed a wide range of particle sizes, from nanome

145 o characterize a broad selection of U.S. fly ashes of varied geological origin in order to rank their

146 To analyze these phenomena, surrogate fly ashes were synthesized to mimic the presence of their ma

147 REEs (Nd, Eu, Tb, Dy, Y, and Er) in the fly ashes was 34-38% of the total and considerably higher th

148 The intrinsic densities of the fly ashes were in the range of 2.7-3.2 g/cm(3).

149 with records of spheroidal carbonaceous fly-ash particles (SCPs), another BC component, for ca. the

150 Pb/(226)Ra ratios greater than 1 in most fly-ash samples.

151 .99 for magnesium and potassium and 0.97 for ash.

152 d 1000 kernel weights whereas a decrease for ash and protein contents by increased maturation level.

153 Using glass powder as surrogate for ash, we experimentally simulate its atmospheric processi

154 sphate (TPP) and 7290 ng/g dw for TBOEP; for ash, they were between 2.17 ng/g dw for TMPP and 427 ng/

155 bromatologic test (dry material) results for ashes, proteins, lipids and carbohydrates revealed 23.4%

156 the lanthanides, yttrium, and scandium) for ashes derived from Appalachian sources was 591 mg kg(-1)

157 nsition metal found in cigarette smoke, fuel ash, mineral ores, and steel alloys.

158 The highest ash content was 3.9% (melon and peach).

159 , sucrose - 100%) (set 2: free acidity, HMF, ash - 95%).

160 react with silica sources, such as rice hull ash, in the presence of NaOH (10%) to form H2O and disti

161 ng cost, partially oxidized "black rice husk ash" containing substantial residual carbon was applied

162 il amendments including rice husk, rice husk ash, and CaSiO3 in a pot study.

163 emains a major source of uncertainty both in ash dispersal forecasting and interpretation of eruption

164 vary, there was a significant difference in ash content according to extraction process and olive va

165 Controls on the soluble Fe fraction in ash remain poorly understood but Fe solubility is likely

166 the genotoxic risk of pollutants present in ash that might be concentrated in animal products and, t

167 mospheric transport before coming to rest in ash fall deposits.

168 s the levels of ADB damage currently seen in ash populations in Southeast England may not be an accur

169 fies inoculum levels of different strains in ash stands.

170 mg kg(-1) and significantly greater than in ashes from Illinois and Powder River basin coals (403 an

171 organic nitrogen (19%-of-control) yields in ashes.

172 its correlated chemical attributes including ash content (AC), antioxidant activity (AA), and total p

173 sect-vectored or water-spread conidia infect ash and may sporulate in planta, as well as in forest de

174 Ash was separated into the acid-insoluble ash (AIA) and acid-soluble ash (ASA) fractions using HCl

175 indings, we propose a mechanism of hail-like ash aggregation that contributes to the anomalously rapi

176 SB presented the highest protein, lipid, ash, beta-glucan, total and insoluble dietary fiber cont

177 Manchurian ash (Fraxinus mandshurica), which coevolved with EAB, is

178 Manchurian ash was less preferred for adult feeding and oviposition

179 tress decreased the resistance of Manchurian ash, but had no effect on constitutive bark phenolics, s

180 rs (total acidity, pH, moisture, dry matter, ash, and qualitative hydroxymethylfurfural) were within

181 ere assessed for basic analyses (dry matter, ash, protein, starch and fat content), total phenolic an

182 The melted ash is simultaneously expelled from the channel by the h

183 Twelve microscopic ash deposits or cryptotephra, invisible to the naked eye

184 Moisture, ash, proteins, lipids and carbohydrate content were 77.5

185 e nutritional and antinutritional (moisture, ash, protein, fructans, dietary fibers, phenolic content

186 acidity, electrical conductivity, moisture, ash, lactonic/free acidity ratio and colour parameters L

187 acidity, electrical conductivity, moisture, ash, lactonic/free acidity ratio and colour parameters L

188 d concentration of macronutrients, moisture, ash, dietary fiber, fatty acids, minerals, carotenoids,

189 Contents of moisture, ash, protein, fat, dietary fibre, inulin, total phenolic

190 compositions (protein, crude oil, moisture, ash and fiber content) of RB.

191 of 7 physico-chemical parameters (moisture, ash, pH, Cu, Fe, Mn and Zn) were determined in 64 sample

192 /-0.07% and 66+/-2%, respectively; moisture, ash, fat, and protein content was 13.8+/-0.5%, 2.6+/-0.7

193 significant (p>0.05) effect on the moisture, ash and fat content on sesame seeds.

194 abies), bird cherry (Prunus padus), mountain ash (Sorbus aucuparia), ground elder (Aegopodium podagra

195 ramme to produce genetically variable native ash tree populations with lower ADB susceptibility may b

196 osition was strongly enhanced by the nuclear ashes of hydrogen burning.

197 h debris and grows in soil in the absence of ash tissues.

198 inated by the fallout of aeolian dust and of ash from occasional volcanic eruptions, indicating that

199 venient method to quantify concentrations of ash, potassium and magnesium and present the potential t

200 Concentrations of ash, potassium and magnesium were determined with refere

201 The red basmati had higher content of ash, protein, fat, TPC, TAC and AOA than white basmati.

202 ted with albedo effects due to deposition of ash sourced from high-latitude volcanic eruptions.

203 In 2013, in response to an epidemic of ash dieback disease in England the previous year, we lau

204 ical of jet engines exacerbate the impact of ash by provoking its melting and sticking to turbine par

205 A considerable high level of ash (2%) and total phenols (3600mg/L as GAE) characteriz

206 ality, a harder texture and higher levels of ash, Ca, Mg and K than those of experimental cheeses A a

207 optera: Buprestidae), has killed millions of ash trees in North America.

208 with chemometrics for at-line monitoring of ash, potassium and magnesium content of GF flours: tapio

209 species that causes widespread mortality of ash.

210 , has severely damaged a large proportion of ash trees (Fraxinus excelsior) in continental Europe.

211 he sudden ejection of this large quantity of ash can perturb the equilibrium of the whole atmosphere

212 al mass erupted to constrain the quantity of ash dispersed in the atmosphere and to efficiently evalu

213 River Ash in northern Europe, recognition of ash from the Oruanui eruption in Antarctica dramatically

214 review the literature on host resistance of ash to emerald ash borer (EAB, Agrilus planipennis), an

215 g(-1), 4.78g.100g(-1) and 90.89g.100g(-1) of ashes, lipids, proteins and total carbohydrates on a dry

216 tous respiratory allergens (ie, grass, olive/ash pollen, house dust mites), specific IgE did not show

217 Differences on ash and protein contents were observed.

218 w that conidia are capable of germination on ash leaves and in vitro, and can infect seedlings via le

219 ated handwashing area near the home, soap or ash were more frequently observed at control households

220 Here, based on experiments, we parameterize ash behaviour and develop a model to predict melting and

221 The invasive pathogen, ash dieback fungus Hymenoscyphus fraxineus, is spreading

222 as up to 45% lower biofilm chlorophyll a per ash-free dry mass, 85% lower biofilm gross primary produ

223 water content, electrical conductivity, pH, ash content, visual appearance and colour intensity.

224 etals (Cr>Cd approximately Pb), and polluted ash induced a strong recApr-Luc2 response.

225 These results indicate that postfire ash loading and algal bloom stage may significantly affe

226 duction may render atmospherically processed ash a significant source of Fe(II) for phytoplankton.

227 Protein, ash and dietary fibre contents increased linearly (P<0.0

228 lose, crude fiber, crude fat, crude protein, ash, AOA, TPC and TAC contents of basmati.

229 chemical variables were determined, protein, ash, chloride, sodium, phosphate.

230 moisture, Brix degree, total fiber, protein, ash, pH, acidity, ascorbic acid, total phenolic compound

231 tive correlation with total solids, protein, ash, Ca, Mg and P contents of soymilk.

232 e studied in terms of pectin yield, protein, ash, non-starch polysaccharide, galacturonic acid (GalA)

233 materials to determine the effects on pseudo-ash samples of simplified composition.

234 built to detect genotoxic hazard in recycled ash.

235 gross primary production, 24% greater seston ash-free dry mass, and 30% lower seston community respir

236 -value trees, and integrated efforts to slow ash mortality.

237 al land or recovering phosphorus from sludge ash, also have limitations.

238 production and the solid residuals of sludge ash and glassy slags would be applied as cementitious ma

239 However, the sewage sludge ash (SSA) is almost completely disposed of and with it a

240 he acid-insoluble ash (AIA) and acid-soluble ash (ASA) fractions using HCl.

241 Furthermore, minerals found in both species ashes were: calcium, potassium, magnesium, iron and phos

242 the ornithine transcarbamylase-deficient Spf(ash) mouse and the neonatal lethal argininosuccinate syn

243 losic biomass, namely, beech, birch, spruce, ash, oak, and pine as well as commercial available softw

244 hod from natural silica source of stem sweep ash (SSA).

245 both species polewards it may alleviate the ash dieback crisis in southern and occidental regions at

246 the pathogen that causes the disease and the ash trees that are devastated by it.

247 d folded into boats, (2) dissolving both the ash and the boat in acid, (3) performing a column separa

248 This decreased the ash content of permeate and converted approximately 17%

249 content and origins of the feed coal for the ash.

250 cosity, AA, and TPC, while GSF increased the ash and total fiber contents of yogurts.

251 A third aircraft was used to measure the ash in situ using optical particle counters.

252 hich temperatures are sufficient to melt the ash, regardless of peak current.

253 Complete dissolution of the ash and low mass boat provided high tracer recoveries an

254 Parboiling reduced the ash content of red rice while no difference was determin

255 M hydrochloric acid for 30 min, in which the ash content was 0.62% (dry weight basis).

256 The fraction of Ag(0) of the total Ag in the ashes was quantified by linear combination fitting (LCF)

257 as identified as a major Ag component in the ashes, and Ag2S was clearly absent.

258 o these elements, via fires, fumes and their ashes, which could have played certain role in environme

259 dissolved organic matter (DOM) levels due to ash input and algal growth in source waters, and consequ

260 ssium (K) is an important element related to ash and fine-particle formation in biomass combustion pr

261 tions suggest that reduced susceptibility to ash dieback may be more widespread in Great Britain than

262 proved markers for reduced susceptibility to ash dieback.

263 onses may underlie reduced susceptibility to ash dieback.

264 optimization was performed to maximize TPC, ash and fibers contents, and sensory acceptance: a yogur

265 ng the extent of the threat of far-travelled ash clouds on flight paths is substantially hindered by

266 Major As-bearing hosts in unamended ashes were glass, iron (oxyhydr)oxides, and calcium arse

267 adar detection and, even in good visibility, ash clouds are difficult or impossible to detect by eye.

268 Volcanic ash from explosive eruptions can provide iron (Fe) to oc

269 n finding ways to identify airborne volcanic ash in order to keep airspace open and avoid aircraft gr

270 lightning discharge, when airborne volcanic ash is transformed into lightning-induced volcanic spher

271 Airborne volcanic ash particles are a known hazard to aviation.

272 tes on stratigraphically bracketing volcanic ash and pyroclastic density current deposits, in combina

273 D) to examine its ability to detect volcanic ash from commercial jet aircraft at distances of more th

274 U-Pb zircon dates for five volcanic ash beds from the Global Stratotype Section and Point fo

275 umber of LIVS typically observed in volcanic ash despite the frequent occurrence of lightning during

276 Key reactants include volcanic ash (source of reactive aluminium) and reactive biogenic

277 n Hemisphere, sub-visible layers of volcanic ash (cryptotephra) are valuable time markers due to thei

278 gether, accelerating the fallout of volcanic ash and climate-forcing aerosols.

279 The ingestion of volcanic ash by jet engines is widely recognized as a potentially

280 l ash cloud created by dispersal of volcanic ash from a second aircraft.

281 Textural analysis of volcanic ash from Santiaguito volcano in Guatemala reveals the pr

282 time, airborne remote detection of volcanic ash has been successfully demonstrated from a long-range

283 ssess the deposition probability of volcanic ash in jet engines.

284 The use of volcanic ash layers for dating and correlation (tephrochronology)

285 the prediction of the behaviour of volcanic ash, leading to overestimates of sticking temperature an

286 f the device to detect and quantify volcanic ash in an artificial ash cloud created by dispersal of v

287 he Amazon basin has been subject to volcanic ash fallout during the recent past; 2) highlights the op

288 the first cryptotephra (non-visible volcanic ash horizon) to be identified in the Amazon basin, which

289 ch affects the temperature at which volcanic ash becomes liquid, can vary widely amongst volcanoes.

290 first identification of New Zealand volcanic ash in Antarctic ice.

291 with black ash (moderate severity) and white ash (high severity) associated with the 2013 Rim Fire in

292 tions [10% and 65% (v/v)] of black and white ash water extracts (BE and WE) to study dynamic changes

293 that the aromaticity of WEOM followed white ash > control > black ash and fluorescence region II (ex

294 Widespread ash dispersal poses a significant natural hazard to soci

295 restimating the long-term risk of widespread ash dispersal for trans-Pacific and trans-Atlantic fligh

296 sight into the form(s) of Fe associated with ash as wet aerosol versus cloud droplet, we improve know

297 Nixtamalization with Ca(OH)2 and wood ashes gave the best viscoelastic characteristics of masa

298 calcium sources: Ca(OH)2 (traditional), wood ashes (classic), CaCO3 (ecological), CaSO4 (ecological),

299 f three nixtamalization processes using wood ashes, Ca(OH)2, and CaCl2 on the physicochemical propert

300 In contrast, cooking with wood ashes and Ca(OH)2 produced denaturation of bean proteins