ライフサイエンスコーパス: ash

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

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

3 We sequenced whole genomic DNA from 1,250 ash trees in 31 DNA pools, each pool containing trees wi

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

5 nificantly higher protein (10.32% vs 9.65%), ash (5.65% vs 5.05%) and oxalates (0.32% vs 0.22%) conte

6 oteins (25 - 55%), carbohydrates (34 - 69%), ash (3-6.5%) and lipids (0.8-5.3%).

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

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

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

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

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

12 fiber (7.08 +/- 0.01 to 16.6 +/- 0.03%) and ash content (0.59 +/- 0.01 to 2.96 +/- 0.10%).

13 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

14 composed of fat (~73%), protein (~19%), and ash (~9%) and contained considerable amounts of calcium

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

16 to have higher protein (48.66 +/- 0.92%) and ash content (4.81 +/- 0.22%) with reduced fat (24.05 +/-

17 Wheat straw biochars and ash exhibited equivalent or marginally higher Si solubil

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

19 g low energy efficiency, CO(2) emission, and ash agglomeration significantly delay the deployment of

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

21 79 seeds and mucilage respectively), fat and ash content.

22 o treated samples, while dry matter, fat and ash was released mostly to liquids in Promod treated sam

23 21% and 2.47% for moisture, protein, fat and ash, respectively.

24 se made with chymosin, but protein, fat, and ash were similar.

25 total carbohydrate, protein, fat, fiber and ash in the range of 7.50-11.75, 71.90-76.38, 6.7-8.0, 1.

26 types were Lund, hydroxy-methyl-furfural and ash content.

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

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

29 showed similar levels of protein, lipid and ash, as well as fatty acid profiles.

30 Fat, dry matter, and ash contents in the control was higher than GWG treatmen

31 revealed that flours presented moisture and ash contents below the recommended maximum limit.

32 ness ranged from 7.3 to 20.1 N, moisture and ash contents ranged from 75.1 to 88.6% and 0.4 to 2.9%,

33 lgae incorporation increased the protein and ash content of the breads.

34 At higher temperatures, crude protein and ash contents increased, whereas total phenolic, flavonoi

35 ant macronutrients, followed by proteins and ash.

36 g 16-18 km above sea level, was ice-rich and ash-poor.

37 imported honey with total acid, sucrose and ash as the parameters mostly distinguishing between the

38 852 protein-coding genes of which 25% appear ash specific when compared with the genomes of ten other

39 ., newly formed carbonates) when samples are ashed.

40 Lake deposits, plant-based ashes, filtrates and evaporites or alkaline salts are us

41 ten neglected in climate simulations because ash particles are assumed to have a short atmospheric li

42 e presence and potential interaction between ash plume, thunderstorm, and PDC transport during this s

43 (CaSiO(3)), fused Ca-Mg-phosphates, biochar, ash, diatomaceous earth, and municipal sewage sludge.

44 ss residues, carbonated agricultural biomass ash-based monoliths have potential as novel low-carbon c

45 reactivity of selected agricultural biomass ashes with CO(2) and their ability to be bound by minera

46 0% w/w CEM 1 was used); furthermore, biomass ashes were a suitable substitute for CEM 1 up to 50% w/w

47 can be applicable to a wide range of biomass ashes in a closed 'emission-capture' process 'loop'.

48 The biomass ashes were moistened (10% w/w) and moulded into cylindri

49 The boiler ash and cement-based waste pretreatments also produced h

50 substrate pretreated with incinerator bottom ash (IBA).

51 ially ice-active minerals in both the bottom ash and emitted aerosol particles.

52 The rice straw ash prepared by ashing unexpectedly had greater adsorption capacity for

53 nd modified rice straw (Ms) were prepared by ashing, pyrolysis and citric acid modification, respecti

54 thogen Hymenoscyphus fraxineus, which causes ash dieback disease.

55 fungus Hymenoscyphus fraxineus, which causes ash dieback.

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

57 Coal ash disposal exposes communities to heavy metals and par

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

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

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

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

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

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

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

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

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

67 ential environmental risks from unlined coal ash ponds.

68 he future spatial distribution of the common ash.

69 reviously characterized in moisture content, ash and nitrogen.

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

71 ighlighted as potential biomarkers in Danish ash trees to differentiate between those tolerant and su

72 s, protein and oil increased then decreased; ash and other carbohydrates decreased; starch increased;

73 Our results show that the explosion-derived ash has an even distribution of plagioclase and glass, b

74 our hypotheses, we found that the developing ash-soil community already showed a similar gene functio

75 s and taxonomic affinities in the developing ash-soils are to some extent distinct from the natural v

76 lerant and susceptible to the fungal disease ash dieback.

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

78 Green ash, the most widely distributed ash species, is severely affected by EAB infestation, ye

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

80 determination was AAS technique, with a dry ashing sample procedure, as a prior treatment.

81 on hardness than phytoliths extracted by dry ashing, we propose that the hydration state of plant tis

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

83 High-purity 69.69 mmol-H(2)/(dry-ash-free)g-brown seaweed is produced with a conversion a

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

85 With the knowledge that emerald ash borer has recently entered Europe from Russia, and t

86 hreatened by the rapid spread of the emerald ash borer (EAB, Agrilus planipennis), an invasive pest f

87 te loci underlying resistance to the emerald ash borer (EAB, Agrilus planipennis), the United States'

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

89 future herbivore threats such as the Emerald ash borer.

90 Populations of European ash trees (Fraxinus excelsior) are being devastated by t

91 in Europe for ash dieback tolerant European ash (Fraxinus excelsior), we undertook comprehensive scr

92 ffered in their proximate composition except ash and fibre contents.

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

94 Protein, fat, ash, lignanamides and proanthocyanidins remained mostly

95 matter, carbohydrate, protein, crude fiber, ash, folic acid, Ca, Mg, Fe, Mn, and Zn increased signif

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

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

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

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

100 ently present within an alkali-activated fly ash (AAF) during in-situ confined compression.

101 d combustion borne particulates, such as fly ash.

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

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

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

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

106 ntration of REEs from a leachate of coal fly ash.

107 re more responsive to capsaicin and coal fly ash.

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

109 long lived sea fish tissue, fossil fuel fly ash contaminated soil and vegetable samples.

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

111 In contrast, an incinerator fly ash pretreatment showed a progressive decrease in methan

112 ng-range transport and wet deposition of fly ash from the combustion of coal (likely from Western Eur

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

114 of rare earth elements (REEs) from coal fly ashes (CFAs) has been considered as a promising resource

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

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

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

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

119 .99 for magnesium and potassium and 0.97 for ash.

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

121 osition of C-CM and C-CF mostly differed for ash and fiber content as compared to C-C.

122 e selection trials are ongoing in Europe for ash dieback tolerant European ash (Fraxinus excelsior),

123 generally can serve as reliable markers for ash dieback susceptibility, there are differences betwee

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

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

126 utrients (protein, oil, starch, beta-glucan, ash and other carbohydrates) and avenanthramides (AVA) 2

127 pig slurry digestate treatments had greater ash content and lower proportions of fixed carbon compar

128 Green ash (Fraxinus pennsylvanica) is an outcrossing, diploid

129 Green ash, the most widely distributed ash species, is severel

130 The genetic linkage map for green ash (Fraxinus pennsylvanica) contains 1201 DNA markers i

131 for genetic studies and improvement of green ash are available.

132 A first genetic linkage map of green ash was constructed from 90 individuals in a full-sib fa

133 The green ash map shows stronger synteny with coffee than tomato.

134 Comparisons of the organization the green ash map with the genomes of asterid species coffee and t

135 from okra, tomato, peanut, Indian hawthorn, ash, willow and elm trees (7 samples); M. marylandi Jeps

136 hisms (SNPs) associated with low versus high ash dieback damage.

137 es (84.81%); a liquid fraction with a higher ash content (11.5%); and a pellet fraction with a higher

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

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

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

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

142 (PMA) to quantify the phase distribution in ash samples collected during activity at Santiaguito, Gu

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

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

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

146 The studied samples were rich in ash, fiber, protein, vitamin C and low in fat.

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

148 The calcia in ashes formed a negative relationship with ash yield and

149 ched the speciation of Cu and Zn observed in ashes from full-scale incinerators.

150 The CO(2) sequestered in ashes (125-414 g CO(2)/kg) and that emitted after incine

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

152 unts of CO(2) (147-424 g equivalent CO(2)/kg ash).

153 ttle or no ash), acid-washed biomass (little ash), and unwashed biomass (range of ash content).

154 unique surface morphology and relatively low ash content.

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

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

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

158 we show that the persistence of super-micron ash is consistent with a density near 0.5 g cm(-3), clos

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

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

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

162 contained considerable amounts of moisture, ash, protein, lipid and carbohydrate but were low in cru

163 /-0.07% and 66+/-2%, respectively; moisture, ash, fat, and protein content was 13.8+/-0.5%, 2.6+/-0.7

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

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

166 MSWI ash management practices in relation to the TCLP, and di

167 g information, example data, and common MSWI ash management practices provide insight into potential

168 In light of the large volume of MSWI ash and the expenses and regulatory burden if this ash w

169 lities place great emphasis on ensuring MSWI ashes pass the toxicity characteristic leaching procedur

170 regulatory driver in the management of MSWI ashes.

171 y recovery ends up as MSW incinerator (MSWI) ash.

172 Native ash species in North America are being threatened by the

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

174 s produced from pure compounds (little or no ash), acid-washed biomass (little ash), and unwashed bio

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

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

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

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

179 t out to estimate the cost of the dieback of ash, Fraxinus excelsior, caused by Hymenoscyphus fraxine

180 est insect to date, within the pan-genome of ash trees (the genus Fraxinus).

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

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

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

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

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

186 (little ash), and unwashed biomass (range of ash content).

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

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

189 not only contained lower AVAs, protein, oil, ash, and other carbohydrates and higher beta-glucan and

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

191 hs with the SO(2) heterogeneous chemistry on ash particles than without.

192 Differences on ash and protein contents were observed.

193 tletoe extracts, including Fraxini (grown on ash trees) and Iscador Q and M (grown on oak and maple t

194 2) lifetime is determined by SO(2) uptake on ash, rather than by reaction with OH as commonly assumed

195 record the global fallout of aerosols and/or ash particles during the eruptions of the CAMP basalts.

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

197 or (3) geophagous materials (clay, soil, or ash).

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

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

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

201 ochemical parameters (moisture, acidity, pH, ash, electrical conductivity, glucose, fructose, hydroxy

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

203 ling, some isolated imports of Islamic plant ash glasses from Mesopotamia, and, most notably, the dev

204 Effluents from coal-fired power plant ash ponds are a major source of environmental contaminat

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

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

207 252.24 +/- 0.11 (2sigma) Ma) from a pristine ash-fall deposit in the Karoo Lystrosaurus AZ.

208 Protein, ash content, redness and yellowness increased while fat

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

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

211 n significantly influences its fat, protein, ash and mineral content but not its AAs' and FAs' conten

212 The moisture, protein, ash, fibre and carbohydrate content varied from 10.84% t

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

214 The macronutrient (total lipids, proteins, ash and carbohydrates) and micronutrient (fatty acids, c

215 Pseudo-ash was manufactured through milling and sieving of erup

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

217 These CO(2)-reactive ashes could mineralise CO(2) gas and be used to cement '

218 The CO(2)-reactive ashes embodied significant amounts of CO(2) (147-424 g e

219 built to detect genotoxic hazard in recycled ash.

220 oo Basin were limited to one high resolution ash-fall deposit in the upper Daptocephalus AZ (253.48 +

221 the relatively moderate pH of the Sakurajima ash, proximity of our mesocosms to propagule sources, an

222 ls, each pool containing trees with the same ash dieback damage status in a screening trial and from

223 Selected ashes were combined with raw biomass and Portland Cement

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

225 in the fruit flesh included soluble solids, ash, flavonols.

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

227 Kelut eruption in 2014, stratospheric ash-rich aerosols were observed for months.

228 traw was used as the control, the rice straw ash (Sa), biochar (Sa), and modified rice straw (Ms) wer

229 The rice straw ash prepared by ashing unexpectedly had greater adsorpti

230 In conclusion, rice straw ash shows the greatest potential of being applied to pad

231 We infer that ash dieback resistance in F. excelsior is a polygenic tr

232 The ash mesocosms also did not show any increased relative a

233 The ash particles resulting from both fragmentation modes ar

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

235 ased with the addition of rice straw and the ash levels increased.

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

237 In contrast, the ash generated during dome collapse has an increased frac

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

239 eruption to 431 +/- 2 CE by identifying the ash layer in a well-dated, high-resolution Greenland ice

240 by immersing an acid-in-oil emulsion in the ash leachate, resulted in similar recovery percentages o

241 In the ash, both Cu (>60%) and Zn (~100%) were coordinated to o

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

243 cling more difficult and arguably making the ash less benign.

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

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

246 sequencing, by 24 months and 36 months, the ash-soil metagenomes already showed a similar diversity

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

248 tning coincided with the rapid growth of the ash cloud, while the second maxima occurred near the tim

249 cause reduction and devolatilization of the ash grains, changing their structural, mineralogical, an

250 Only the ash (p = 0.4314) and nitrogen-free extract (p = 0.4871)

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

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

253 didate genes for defence response within the ash genus could inform breeding for EAB resistance, faci

254 The chemical speciation of Cu and Zn in the ashes was independent of whether they were spiked in the

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

256 t work investigates biomass wastes and their ashes for re-use in combination with mineralised CO(2) i

257 uption from Ilopango volcano deposited thick ash over much of El Salvador when it was inhabited by th

258 d the expenses and regulatory burden if this ash were managed as a hazardous waste, U.S.

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

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

261 proved markers for reduced susceptibility to ash dieback.

262 xtracts of trees tolerant and susceptible to ash dieback sampled from sites in the UK and Denmark.

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

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

265 lor characteristics (a*, b*, and L* values), ash, moisture, protein, oil, total phenolic, and antioxi

266 Volcanic ash from a vulcanian explosion and from a pyroclastic de

267 Volcanic ash is often neglected in climate simulations because as

268 Volcanic ash particle properties depend upon their genetic fragme

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

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

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

272 esocosms of sterile, freshly fallen volcanic ash from the Sakurajima volcano, Japan.

273 Coarse-grained volcanic ash leads to significantly higher complexity, while fine

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

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

276 meter) analyses of five microscopic volcanic ash (cryptotephra) particles extracted from the ice inte

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

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

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

280 l simulations, and of the impact of volcanic ash on stratospheric chemistry and radiation.

281 stages of soil biota development of volcanic ash, and how rapidly it can proceed.

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

283 o identify generation mechanisms of volcanic ash, which is pertinent to volcanology, aviation, respir

284 pulse experiments were performed on volcanic ash samples to determine the magnetic effects that may r

285 nd-sized mineral abrasives (quartz, volcanic ash, loess, kaolin) on DMT in a controlled feeding exper

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

287 s in central volcanoes and from small-volume ash-layers in the associated lava fields.

288 ls) sourced in India, Africa and the UK were ashed and exposed to CO(2) gas.

289 pal nutrient variability of brown rice were: ash (13% c.

290 xtracted from bryophyte material through wet-ashing was described, focusing on abundance, classifying

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

292 Widespread ash dispersal poses a significant natural hazard to soci

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

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

295 in ashes formed a negative relationship with ash yield and the microstructure of the carbonate-cement

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

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

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

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

300 The yield, ash and protein contents of WJP ranged between 4.88-7.87