ライフサイエンスコーパス: volatilization

1 from 18 to 94 for 2,4,6-TBA, indicating net volatilization.

2 plicating combustive formation versus simple volatilization.

3 annot correctly cover the moisture effect on volatilization.

4 ur/Se metabolism yet was found to mediate Se volatilization.

5 quid extraction or chemical/heat-facilitated volatilization.

6 significantly increased Se accumulation and volatilization.

7 almost complete loss in its capacity for Se volatilization.

8 natures of limited partial melting or impact volatilization.

9 the rate of metabolic loss, and the rate of volatilization.

10 otecting acetaldehyde from overoxidation and volatilization.

11 s) that also correlated with greater dicamba volatilization.

12 de-amine salt formulations undergo extensive volatilization.

13 ent to enhance organic matter extraction and volatilization.

14 rely kinetic Zn isotope fractionation during volatilization.

15 y removing the voltage bias, which stops its volatilization.

16 table, which corresponded to greater dicamba volatilization.

17 predict their potential to prevent herbicide volatilization.

18 atile chemicals can largely be influenced by volatilization.

19 ulic retention time of the lake, followed by volatilization.

20 aerobic disposal intended to promote arsenic volatilization.

21 d microbial mercury reduction and subsequent volatilization.

22 the lakes were acting as sources of PCMs via volatilization.

23 quids, which have an air-side limitation for volatilization.

24 SM at the plot scale were degradation (71%), volatilization (5%), leaching (8%) and runoff (3%), whil

25 , nitric oxide (+66%) emissions, and ammonia volatilization (+74%), bringing tropical agricultural ni

26 estrial materials; however, none fingerprint volatilization, a key process that occurs during large b

27 . putida showed high arsenic methylation and volatilization activity.

28 number of special experiments precluded IMI volatilization and contact or oral action of IMI upon ex

29 methylnaphthalene contributed to most of the volatilization and deposition (6.3-89%) before and after

30 idative stability, providing protection from volatilization and environmental conditions.

31 derestimates VOC emissions from drilling mud volatilization and flowback green completions.

32 Both volatilization and foliar penetration affect the measure

33 es were in the two-film model for predicting volatilization and in microbial degradation rates.

34 artially removed from fresh THS specimens by volatilization and oxidation, but it was not significant

35 of oxygen concentrations due to simultaneous volatilization and oxidation.

36 e needed to understand and predict pesticide volatilization and persistence in agroecosystems.

37 e polymer and other additives can affect BFR volatilization and reactivity.

38 ariations, suggesting a seasonal cycle of Se volatilization and recondensation.

39 ns tested, the most effective in terms of Se volatilization and Se removal from the water column was

40 nd with correction for compound loss through volatilization and sorption.

41 n suggests that aerosols are not a result of volatilization and subsequent nucleation of ABS or direc

42 rbon-rich water body might be eliminated via volatilization and subsequent reaction with gas-phase (*

43 s, we proposed that neutral amines dominated volatilization and that higher temperatures altered thei

44 Pesticide volatilization and vapor drift can have adverse effects

45 redictions showed flushing promoted chemical volatilization, and contaminants did not appreciably sor

46 ntributed by advection, molecular diffusion, volatilization, and flow regime within the PAS, finding

47 oss, clogging of collection systems, ammonia volatilization, and odor nuisance.

48 n the atmosphere as a result of spray drift, volatilization, and suspension of coated soils.

49 s on nitrous oxide (N(2)O) emission, ammonia volatilization, and the performance of pearl millet [Pen

50 microenvironmental transport and deposition, volatilization, and transfer of pesticide when passenger

51 mistry in China we found that deposition and volatilization are key factors controlling distribution

52 determine their ability to control herbicide volatilization are poorly understood.

53 Because of issues such as adsorption/volatilization artifacts, it faces obstacles in measurin

54 ys to inform about the compound loss through volatilization as a confounding factor.

55 d by temperature-dependent processes such as volatilization at warm temperatures.

56 bines (a) multiphase partitioning to predict volatilization, (b) a new kinetics module for predicting

57 emitted during transient cycles showed that volatilization began at around 40 degrees C, with the ma

58 With use of TGA and XRD the volatilization behavior of Mo was studied.

59 to enhance rates of contaminant removal via volatilization, but the magnitude of different volatiliz

60 e), but also a fluctuation of cropland NH(3) volatilization by -1.9-4.7 Tg N yr(-1) (-12%-31% change)

61 Se volatilization by Indian mustard accounted for only 0.7%

62 se herbicide solubility and reduce herbicide volatilization by producing herbicide-amine salts.

63 Arsenic volatilization can be mediated by the enzyme arsenite S-

64 e can be emitted, clearly demonstrating that volatilization can occur via processes unrelated to sunl

65 Volatilization causes changes in the isotopic compositio

66 a L.) production are lost due to leaching or volatilization, causing severe environmental pollution a

67 of raw dairy manure slurry decreased ammonia volatilization compared with surface application.

68 is of arsM expression, revealed that arsenic volatilization correlated with methanogenic activity.

69 ticular ability for BAPMA to control dicamba volatilization could be attributed to several molecular

70 NO(3)(-) volatilization could only explain 0.9-15% of NH(4)(+) lo

71 the model is the 24 h cumulative percentage volatilization (CPV(24h)) loss.

72 em and to predict 24-h cumulative percentage volatilization (CPV(24h)) losses.

73 rations close to soil-air equilibrium or net volatilization depending on chemical volatility.

74 The inhibitory effect of NBPT on ammonia volatilization did not improve with NBPT concentration i

75 Impact-induced volatilization drives volatile depletion in asteroidal p

76 cools during microwave-assisted evaporation, volatilization due to overheating at dryness is minimize

77 corresponds to the expected increase in PCB volatilization due to the effect of temperature on vapor

78 the K-Pg boundary layer, thus earmarking Zn volatilization during impact and subsequent ejecta trans

79 artz ampules to minimize the loss of Re from volatilization during melting at 1000 degrees C.

80 d p,p'-dichlorodiphenyldichloroethane), with volatilization during the day and deposition in the nigh

81 ace analysis, where losses of analyte due to volatilization during the evaporation process are minimi

82 nduce major SEI evolution from reactions and volatilization during XPS(1,2).

83 ir model allowed a better description of the volatilization dynamics on a diurnal cycle (increasing e

84 The larger volatilization estimate at Travis was expected because o

85 In the current study, open-system volatilization experiments (focusing thereby on kinetic/

86 Fractionation of CFCs in volatilization experiments from pure-phase CFC-11 and CF

87 Based on volatilization experiments, emission of DMS to the atmos

88 uced an increase of 8% in the averaged total volatilization flux, however this effect can be neutrali

89 Volatilization fluxes of HHCB ranged from 11 +/- 6 to 34

90 her evidenced by the correlation between net volatilization fluxes of PCBs and seawater salinity.

91 technique provides an estimate of potential volatilization fluxes without relying on enclosure-based

92 mass spectrometers typically employ analyte volatilization followed by electron ionization or chemic

93 is, the one-dimensional model for pesticide volatilization following application on bare soil (Volt'

94 fic seasonal delta(15)N values of soil NH(3) volatilization for reliable regional seasonal NH(3) sour

95 Water-air fugacity ratios indicated net volatilization (FR > 1.0) or near equilibrium (FR not si

96 Ammonia (NH(3)) volatilization from agricultural lands is a main source

97 us close to air-surface equilibrium to a net volatilization from Antarctic reservoirs.

98 s faster, compared to the likely kinetics of volatilization from aqueous systems.

99 Pesticide volatilization from bare soil exhibits usually a diurnal

100 atile organic compounds (VOCs) pollution and volatilization from complex groundwater systems on surfa

101 Cs), only hypothetical emissions via passive volatilization from e-waste were considered whereas for

102 from the location of detection and continued volatilization from existing in-use products and waste s

103 from DMSeP because DMSeP was the rate of Se volatilization from faster than from SeMet and SeMet (bu

104 NH(3) volatilization from fertilizers and wastes (v-NH(3)) has

105 nintentional damage to vegetation due to its volatilization from genetically engineered dicamba-toler

106 Amine volatilization from herbicide-amine salts may additional

107 Ammonia volatilization from incubated soil ranged from 140 g kg(

108 Trichloroethylene (TCE) volatilization from leaves, trunk, and soil was measured

109 ovel genes whose products are involved in Se volatilization from plants, a broccoli (Brassica olerace

110 d in the literature for these compounds, for volatilization from pure liquids.

111 To determine the rate-limiting steps in Se volatilization from selenate and selenite, time- and con

112 Our data suggest that Se volatilization from selenate is limited by the rate of s

113 Se volatilization from selenite may be limited by selenite

114 In this study, we measured dicamba volatilization from solid (BAMPA) on glass as with dimet

115 Bs in Zurich are probably released mainly by volatilization from sources that are directly exposed to

116 urden of organic UV-filters are explained by volatilization from terrestrial and aquatic surfaces and

117 the basis of the scaled field measurements, volatilization from the leaves and soil may play a signi

118 eric deposition has become negligible, while volatilization from the water surface is still a major r

119 inhibitor product Limus((R)) to decrease NH3 volatilization from urea applied to maize.

120 cids, however, have relatively high KAWs and volatilization from water has been demonstrated.

121 and the output flows due to sediment burial, volatilization from water to air, and transport to Lake

122 of vapor-phase samples, two modes of sample volatilization (heated capillary and thermal desorption

123 enol C6H4N2O5) measured with a micro-orifice volatilization impactor (MOVI) high-resolution chemical

124 BoCOQ5-2 was found to promote Se volatilization in both bacteria and transgenic Arabidops

125 The model captures the general trend of the volatilization in different humidity scenarios.

126 xhibits strong isotopic fractionation during volatilization in planetary rocks, but is hardly fractio

127 Dicamba volatilization in the field is also expected to occur af

128 developed that enabled consideration of the volatilization in the modeling of degradation kinetics.

129 pplied was lost (presumably because of NH(3) volatilization) in contrast to far greater losses report

130 elenite-supplied plants, Se accumulation and volatilization increased linearly with external Se conce

131 proposed to account for mass removal and for volatilization into the headspace.

132 fluorescent labeling based on probe molecule volatilization is developed.

133 dditional amines, we determined that dicamba volatilization is primarily influenced by the number of

134 In Central China the rate of soil Se volatilization is similar to that of Se deposition, sugg

135 crop plants, while the rest is lost through volatilization, leaching, and surface run off.

136 ilizer granules are lost continuously due to volatilization, leaching, denitrification, and surface r

137 ted urea was ineffective in reducing ammonia volatilization loss and improving N nutrition, grain yie

138 eated urea and PCU reduced the total ammonia volatilization loss by 29.1-78.8%, 35.4-81.9%, 77.3-87.4

139 Sorption to sludge and biodegradation and/or volatilization losses are important factors that affect

140 and the conditions under which the greatest volatilization losses exist were easily identified using

141 Pesticide volatilization losses from soil, calculated with the new

142 curately model literature-reported pesticide volatilization losses from soils.

143 observed, and the new setup ensured that the volatilization losses were kept below the mineralized fr

144 Volatilization losses were minimal for all compounds tes

145 Plant Se accumulation and volatilization may be applied in crop biofortification a

146 f the lakes' coastal boundary zone suggested volatilization may be responsible for the loss of 64-213

147 latilization, but the magnitude of different volatilization mechanisms, and the relationship between

148 itudes of gas-phase and transpiration-driven volatilization mechanisms.

149 involved in sulfur/selenium assimilation and volatilization, methylation of selenocysteine, and conve

150 then used as input parameters in a pesticide volatilization model to understand how their variability

151 The Pesticide Loss via Volatilization model was developed to predict and unders

152 quation and a previously described pesticide volatilization model, were compared to previous results

153 fitting the experimental measurements with a volatilization model.

154 ndence on the hydration status into a simple volatilization model.

155 However, established volatilization models do not explicitly consider the hyd

156 y conditions can be integrated into existing volatilization models that already work well for humid c

157 vironmental factors, on soil N losses (NH(3) volatilization, N(2) O emissions, and N leaching) and cr

158 experimental conditions, and this is due to volatilization, not oxidation.

159 The largest PAH volatilizations occurred at the sites in Alabama and Mis

160 The largest PAH volatilizations occurred at the sites in Alabama and Mis

161 relationship expected due to the progressive volatilization of (14)N rich ammonia from decomposing gu

162 dspace analysis is used widely and relies on volatilization of analytes into the headspace above the

163 rs) to near-shore Lake Ontario compared with volatilization of approximately 6 kg y(-1) of mainly lig

164 essed, which was ascribed to photo bleaching/volatilization of BrC and/or due to rising boundary laye

165 % of bromine fluxes from previously reported volatilization of bromomethanes and bromochloromethanes.

166 sed formulations are widely used to decrease volatilization of carboxylic acid-containing herbicides

167 evation in the pH of the droplets, caused by volatilization of CO(2) from bicarbonate buffer within t

168 urements, and used to predict plant-mediated volatilization of common VOCs as well as quantify the co

169 per thousand and -1.9 per thousand) and for volatilization of compounds dissolved in water (-4.4 per

170 m for nanoparticle formation was heat-driven volatilization of cyclic siloxanes and various low-volat

171 e speculate that after rupture, preferential volatilization of delta(15)N-depleted compounds (especia

172 e-amine salts may additionally contribute to volatilization of dicamba and 2,4-D.

173 ndosulfan (-0.02 to -33 ng/m(2)/day) and net volatilization of heptachlor, aldrin, trans-chlordane, a

174 promising technique for gentle and efficient volatilization of intact organic molecules from surfaces

175 Volatilization of lower-chlorinated polychlorinated biph

176 Volatilization of Me2AsH and TMAs(III) from contaminated

177 e of unrecorded (contra-band) production and volatilization of mercury during processing and recovery

178 after DMF evaporation is critical to prevent volatilization of metal containing species.

179 The huge isotopic spread is explained by volatilization of metal halides during basalt eruption--

180 high surface area-to-volume ratios, however, volatilization of NO(y) photoproducts is favored, and NO

181 Craig-Gordon isotope model is valid for the volatilization of nonpolar organic liquids with air-side

182 narios, such as isotope fractionation during volatilization of organics from open water surfaces, hav

183 zation of the CD structure, characterized by volatilization of over 60% of nascent carbon atoms and t

184 e and Eagle Harbor sites generally displayed volatilization of PBDEs into the atmosphere, mainly BDE-

185 e/snow-covered conditions toward a clear net volatilization of PCBs and most of the OCPs during snow/

186 ction of the tropical Atlantic suggested net volatilization of PCBs to the atmosphere.

187 Results show that volatilization of pesticides from soil largely exceeded

188 Volatilization of pesticides from the bare soil surface

189 The extent of volatilization of PFCAs in the environment will depend o

190 We suggest that both deposition and volatilization of Se could play a key role in Se balance

191 oxic forms of Se by promoting the biological volatilization of Se.

192 rate-limiting steps for the assimilation and volatilization of selenate to dimethyl selenide (DMSe):

193 Biological volatilization of selenium, Se, in a contaminated area i

194 can produce both the hot, CO2-rich fluid (by volatilization of surface carbonates or other CO2 source

195 k for evaluating the potential importance of volatilization of TCE and similar compounds at phytoreme

196 porally and spatially to estimate the annual volatilization of TCE at the Travis (0.82 +/- 0.51 kg/yr

197 phase interface causes local heating and the volatilization of the analyte species.

198 icide vapor drift is a two-step process: (a) volatilization of the applied pesticide to vapors and (b

199 que is directly on-line and does not require volatilization of the eluent.

200 The results demonstrate that volatilization of the four halogenated compounds from wa

201 Estimated increased volatilization of the postemergent herbicide S-metolachl

202 EMPI covers a larger m/z range than external volatilization of the sample prior to introduction to th

203 n methods poses recovery problems because of volatilization of the target analyte as the chloride or

204 a 1-3 orders of magnitude enhancement in the volatilization of these analytes and shorter fiber expos

205 assessed by comparing with two data sets on volatilization of trifluralin applied to bare soil.

206 non-irradiated fuel, suggesting non-uniform volatilization of U from melted fuels with different lev

207 rk that transpiration is the main driver for volatilization of VOCs, but also demonstrate that vapor-

208 to that of Se deposition, suggesting that Se volatilization offsets it's deposition, resulting in neg

209 It is likely that the volatilization or decomposition of soluble compounds and

210 om bronchial epithelial cells was lost after volatilization or lyophilization treatment.

211 studies have focused mostly on pure compound volatilization or on compounds dissolved in organic liqu

212 direct use has several disadvantages such as volatilization or oxidation.

213 in, PBDEs may become bioaccessible following volatilization or polymer deterioration.

214 electric furnace heating, such as the severe volatilization, owing to the mismatch of the sublimation

215 This study dealt with the volatilization part alone.

216 microbially mediated mercury methylation and volatilization pathways in polar marine environments.

217 ll as quantify the contribution of different volatilization pathways.

218 Volatilization PCB fluxes were calculated using the modi

219 the mechanistically based description of the volatilization process under dry conditions.

220 es over the Indian and Southern Ocean, while volatilization processes and additional atmospheric emis

221 ce the availability of Hg for methylation or volatilization processes and has substantial potential t

222 The likely changes in volatilization/PVD under climate change were estimated a

223 halene was the PAH with the highest observed volatilization rate of 52000 ng/m(2) day(-1) in June 201

224 hthene was the PAH with the highest observed volatilization rate of 6800 ng/m(2)/day in September 201

225 A study of the volatilization rate of the nerve agent VX (O-ethyl S-2-(

226 anic liquids with air-side limitation of the volatilization rate.

227 ion mechanisms, and the relationship between volatilization rates and contaminant physiochemical prop

228 eveloped to predict and understand pesticide volatilization rates from a planted agricultural field.

229 ), and leaf height (h(leaf)) strongly affect volatilization rates of plant- and soil-sorbed pesticide

230 tand how their variability affects pesticide volatilization rates under different conditions.

231 readily from plants than from soil and that volatilization rates vary significantly for certain pest

232 Se-volatilization rates were 2- to 3-fold higher from plant

233 h external Se concentration up to 20 &mgr;M; volatilization rates were also linearly correlated with

234 s below 24.5 degrees C, modeled chlorpyrifos volatilization rates were higher in the presence of adju

235 nium accumulation and up to threefold faster volatilization rates.

236 indicating that water primarily delays NH(3) volatilization rather than permanently reducing total em

237 cy by manipulating the N-centered annulation-volatilization reactions and C-based sp(3)/sp(2) configu

238 Strategies to reduce dicamba volatilization rely on the use of formulations containin

239 ates using the two-film model suggested that volatilization removes 980-1360 kg of total BAs from Bot

240 the environment through runoff, leaching and volatilization, resulting in three-dimensional (3D) poll

241 Four approaches for pesticide volatilization screening based on Fick's Law were invest

242 a pyrolysis temperature of 1300 degrees C, a volatilization temperature of 2300 degrees C and Mg as a

243 ing the most significant inhibition halos in volatilization tests.

244 APMA had a greater ability to lessen dicamba volatilization than DMA or DGA.

245 m N retention and partitioned more losses to volatilization than estimated from observed N budgets of

246 vironmental fate of PFAMs is suggested to be volatilization to the atmosphere followed by oxidation b

247 tigate potential transfer up the food chain, volatilization to the atmosphere, as well as direct phyt

248 within 72 h, with up to 61% being removed by volatilization to the atmosphere.

249 issions, nitric oxide emissions, and ammonia volatilization totaling more than 1,000 observations.

250 r to simulate on line in situ derivatization-volatilization-transfer steps.

251 drolysis and the associated risk for ammonia volatilization, uncontrolled precipitation, and malodor.

252 plant selenium accumulation, tolerance, and volatilization: upregulation of genes involved in sulfur

253 aluate the role of methanogenesis in arsenic volatilization using methanogen inhibitors.

254 A numerical model for vegetation-mediated volatilization was developed, calibrated with tracer mea

255 throughout leaf development, and monoterpene volatilization was found to occur at a very low rate, wh

256 Arsenic volatilization was highest in methanogenic mesocosms, bu

257 Volatilization was negligible (<0.04%).

258 Volatilization was primarily through the leaf (0.34 +/-

259 sent for every 10 dicamba molecules, dicamba volatilization was still decreased by 70% relative to th

260 Volatilization was the main removal process for both iso

261 loss of lighter Si isotopes during planetary volatilization were also influential in establishing the

262 on-dependent kinetics of Se accumulation and volatilization were studied in Indian mustard (Brassica

263 o the shoot, away from the root, the site of volatilization, whereas only approximately 10% of the se

264 Biologically based Se volatilization, which converts Se into volatile compound

265 type and was defective in elemental mercury volatilization, while the merR mutant was mercury resist

266 e to incomplete solubilization and potential volatilization, whilst other methods may require large,

267 which combines direct particle sampling and volatilization with online chemical ionization mass spec