ライフサイエンスコーパス: photolysis

1 m properties (e.g., rapid hydrolysis or slow photolysis).

2 ecreases by over 4 orders of magnitude after photolysis.

3 nced formation of novel DBPs during chlorine photolysis.

4 pression of Zn(2+)-responsive proteins after photolysis.

5 nsertion products into CH and OH bonds under photolysis.

6 R domains until exposure to light causes its photolysis.

7 nment and imposes matrix effect on HNO(3(s)) photolysis.

8 (-1), respectively) driven by HOCl and Cl(2) photolysis.

9 roteins could subsequently be deprotected by photolysis.

10 icone rubber films using feedback-controlled photolysis.

11 ntify contributions from direct and indirect photolysis.

12 omethane formation decreases during chlorine photolysis.

13 eliminated using chromophore-targeted laser photolysis.

14 were rapidly photoenhanced, followed by slow photolysis.

15 on intermediates, were investigated by flash photolysis.

16 arine boundary layer via particulate nitrate photolysis.

17 as volcanic sulfate aerosols formed from OCS photolysis.

18 sence of light is observed after the initial photolysis.

19 ition of SOA but not chemical losses such as photolysis.

20 these optical probes is bio-inertness before photolysis.

21 active than the methyl radical formed by SAM photolysis.

22 action with [Ru(bpy)(3)](3+) formed by flash photolysis.

23 y revert directly and indirectly to Hg(0) by photolysis.

24 lNO(2) photolysis are 42% and 62% and by ICl photolysis 35% and 28%, respectively.

25 the potential to enable efficient asymmetric photolysis, a method of chiral separation that has conve

26 Ventilation and photolysis accounted for <50% and <0.1% total loss of bl

27 Radical reactions (indirect photolysis) accounted for approximately 50% of chloramin

28 accurately predicts PAA decay under UV(254) photolysis across varying PAA and H(2)O(2) concentration

29 , DOM transformation primarily due to direct photolysis alters DOM such that it is more reactive with

30 rocatechol was mainly detected during direct photolysis and 2,8-dichlorodibenzo-p-dioxin was only fou

31 t the aromatic products of TFM undergo rapid photolysis and emphasizes that niclosamide degradation i

32 Both photolysis and flash vacuum pyrolysis (FVP) of tetrazole

33 the troposphere whereas 2M3P is lost by both photolysis and gas phase reaction with atmospheric oxida

34 lenges, we synthesized and characterized the photolysis and hydrolysis of NB moieties containing diff

35 ter bond exhibited significant rates of both photolysis and hydrolysis, whereas, importantly, the NB

36 cloud-free scenario and reveal that ClNO(2) photolysis and ICl photolysis are crucial for gas-phase

37 After the photolysis and photoelimination of the l-N(3), we initia

38 2 production mechanisms in comets, including photolysis and radiolysis of water, solar wind-surface i

39 determination of total N-nitrosamines by UV-photolysis and subsequent chemiluminescence detection of

40 s are needed that accurately predict oxidant photolysis and subsequent radical reactions.

41 configuration, we investigate the effects of photolysis and the binding of amino acid residues in cyt

42 able family of diazo compounds using flow UV photolysis and their first use in divergent protodeboron

43 QMs were detected by laser flash photolysis and their reactivity with nucleophiles invest

44 NMR, fluorescence quenching, and laser flash photolysis and various degrees of success has been achie

45 bromine trapping experiments and laser flash photolysis, and a mechanism is proposed.

46 ctivation of a single synapse with localized photolysis, and fast imaging of neuronal Ca(2+) signalli

47 een different photochemical pathways (direct photolysis, and indirect photochemistry triggered by dif

48 ) in aqueous solution by ozone, UV-C(254 nm) photolysis, and the corresponding advanced oxidation pro

49 he cloud and cloud-free scenarios by ClNO(2) photolysis are 42% and 62% and by ICl photolysis 35% and

50 o and reveal that ClNO(2) photolysis and ICl photolysis are crucial for gas-phase Cl atom activation.

51 ormation of the products during steady-state photolysis are further established by picosecond laser f

52 The organic radicals generated during photolysis are indiscriminate, leading to a large mixtur

53 etailed kinetics and mechanisms of HNO(3(s)) photolysis are still not clear.

54 rmation of reactive oxidants during chlorine photolysis as a function of pH (6-10) and irradiation wa

55 ength, has been investigated by steady-state photolysis, as well as femtosecond and nanosecond transi

56 us photochemical aging (aging by UVB and UVA photolysis; as well as OH oxidation), as well as aging b

57 mation of the six fluoroquinolones by direct photolysis at 253.7 nm were determined for the pH 2-12 r

58 the intrinsic reactivity of [(3)H]CMPI upon photolysis at 312 nm to identify its binding sites inTor

59 indeed released up to 27 leaving groups upon photolysis at 360 nm.

60 ibenzo-p-dioxin was only found during direct photolysis at pH 8.

61 Subsequent OH(*) oxidation and direct photolysis both decompose the organic nitrates (ONs, rep

62 n considered a very minor channel in nitrate photolysis, but our results indicate it is as important

63 rations of oxidants via H(2)O, O(2) and O(3) photolysis by low-pressure-Hg-lamp emissions and reach h

64 l (PRP) undergoes photodegradation by direct photolysis, by reactions with (*)OH and CO3(*-), and pos

65 In addition, photolysis can also be utilized for the fabrication of c

66 Direct photolysis can be an important degradation pathway for s

67 Degradation of dimethyl disulfide by direct photolysis caused a small but significant MIF (Delta(33)

68 The addition of photolysis causes a ~50% reduction in biogenic SOA loadi

69 Upon photolysis, complex 2 undergoes NO dissociation to yield

70 Under UV-C(254 nm) photolysis conditions, no significant effect of H2O2 add

71 he confined micellar media, with laser flash photolysis corroborated with an external magnetic field

72 surface, we propose that particulate nitrate photolysis could be a substantial tropospheric nitrogen

73 y an important fate for NO3 indoors, but NO2 photolysis could be an important source of indoor O3.

74 The recorded microsecond flash photolysis data were subjected to detailed global target

75 Our strategy is complemented with flash photolysis data, where the lifetimes of different photoi

76 ith copper monochloride or triiodide, the UV-photolysis does not require chemicals and is not affecte

77 olysis in the morning and higher ones of ICl photolysis during afternoon.

78 The photolysis effective quantum yields of PF-2M3P, PF-3M2B,

79 e reactive oxidants produced during chlorine photolysis effectively degrade organic contaminants duri

80 Hammett correlation analysis suggested that photolysis efficiency is favored by electron-rich substi

81 the basis of Fmoc-tBu SPPS compatibility and photolysis efficiency.

82 Additionally, steady-state photolysis, electrochemistry, and laser time-resolved sp

83 and 2.2 +/- 0.4% of nitrogen dioxide (NO(2)) photolysis, equivalent to average atmospheric lifetimes

84 g optoelectronic applications, such as water photolysis, exciton fission and novel photovoltaics invo

85 OA loadings over the Amazon, indicating that photolysis exerts a substantial control over the atmosph

86 The presence of 1 in the photolysis experiment is confirmed by trapping experimen

87 ed good absorption characteristics for flash photolysis experiments in a flow system, with transient

88 Laser flash photolysis experiments led to the characterization of bo

89 Thermolysis and photolysis experiments suggest that the U-Pn bonds degra

90 urther established by picosecond laser flash photolysis experiments.

91 to antioxidant quenching during steady-state photolysis experiments.

92 y means of both steady state and laser flash photolysis experiments.

93 y means of both steady state and laser flash photolysis experiments.

94 eous conditions was examined via laser flash photolysis experiments.

95 e of the water on Mars was lost to space via photolysis following the collapse of the planet's magnet

96 with recent measurements using diiodomethane photolysis for CH2OO generation.

97 enzymes reveals two enzyme classes: in one, photolysis forms 5'-dAdo., and in another it forms .CH(3

98 ived species, meteorological parameters, and photolysis frequencies.

99 ENDOR and EPR measurements show that photolysis generates a new FeMo-co state, denoted E4(2H)

100 Laser-induced hydrogen peroxide photolysis generates hydroxyl radicals that react with s

101 ed OH(X) super rotors identified at 115.2 nm photolysis have an internal energy of 4.86 eV.

102 eterogeneous processes such as oxidation and photolysis have been evidenced by experiments, most theo

103 he molybdenum center can be achieved by post-photolysis heating at convenient temperatures.

104 s, likely the result of reduced dilution and photolysis impacts.

105 l framework was established to simulate HONO photolysis in a room and subsequent reactions associated

106 that dichloroacetamide safeners can undergo photolysis in environmental systems over relevant time s

107 eed for the inclusion of particulate nitrate photolysis in future models for O3 and for the photolysi

108 for estimating contaminant loss via indirect photolysis in lakes.

109 dihydro-1H-cyclopropa[l]phenanthrene undergo photolysis in solution at ambient temperature to produce

110 Hg(0) being the main photoproduct of Hg(II) photolysis in the atmosphere, which significantly increa

111 lations show larger contributions of ClNO(2) photolysis in the morning and higher ones of ICl photoly

112 itrile (DMABN), was subjected to laser flash photolysis in the presence and absence of various model

113 lazole were more slowly degraded by indirect photolysis in the presence of the photosensitizers nitra

114 ded, OH and NO generation by organic-nitrite photolysis in the UVA range is preferable.

115 erically-relevant non-OH chemistry (e.g. VOC photolysis in UVA and UVB) is not sufficiently represent

116 implemented combined two-photon imaging and photolysis in vivo to monitor and manipulate neuronal ac

117 s suggest that, following cleaning, H(2)O(2) photolysis increased OH concentrations by 10-40% to 9.7

118 This study investigated the HONO-photolysis-induced formation of indoor OH, the transform

119 iogenic volatile organic compounds undergoes photolysis-induced mass loss at rates between 0 and 2.2

120 Therefore, photolysis inside leaves may be an important, yet under-

121 Photolysis is a major removal pathway for the biogenic g

122 Chlorine photolysis is an advanced oxidation process which relies

123 Photolysis is not likely an important fate for NO3 indoo

124 We find that HONO photolysis is the dominant contributor to hydrogen oxide

125 The results showed that photolysis is the dominant loss pathway of PF-2M3P and P

126 lly relevant peptides and characterize their photolysis kinetics in both UV- and two-photon-mediated

127 etyl and acetyl radicals produced during the photolysis (lambda >= 305 nm) of 5-100 mM PA under stead

128 OH radical and O(3) reactions, together with photolysis, lead to diminished light absorption and lowe

129 irectly observed upon nanosecond laser flash photolysis (LFP) of 1.

130 Laser flash photolysis (LFP) was used to determine the lifetime and

131 ng fluorescence measurements and laser flash photolysis (LFP).

132 The photolysis lifetimes for the ONs and for the absorbance

133 fluoxetine (NFLX) proved to be a minor TP in photolysis (<=2% of degraded FLX).

134 l Mechanism suggest that particulate nitrate photolysis mainly sustains the observed levels of nitrou

135 ectrometric, electrophysiological, and flash photolysis measurements after its cotranslational insert

136 second transient-absorption and steady-state photolysis measurements show that the electrodes functio

137 ies, such as core hole clock and laser flash photolysis measurements, we have completed a comprehensi

138 The photolysis mechanism was investigated, and the results o

139 were obtained using transmission laser flash photolysis methods by taking advantage of aqueous nanocr

140 Anaerobic steady state photolysis of "light-sensitive" EtPhCbl results in the f

141 Photolysis of 1 at 470 or 530 nm caused N2 elimination a

142 Photolysis of 1 using long-wavelength UVA (365 nm) or vi

143 al substrate, isotope-labeled CPA, following photolysis of 1, 2, and Ru catalyst provides strong evid

144 Photolysis of 1-(1-phenylethylidene)-1a,9b-dihydro-1H-cy

145 generation of dG(N2-H)(.) in high yield via photolysis of 1.

146 horizontal lineN-CH3) is only obtained from photolysis of 1b.

147 viously unreported, was not present with the photolysis of 2, which released thymidine exclusively wi

148 tive o-quinodimethanes (photoenols), and the photolysis of 2,5-diphenyltetrazoles, affording highly r

149 We performed UV-mediated photolysis of 25 different azF-labeled AT1Rs to cross-li

150 Photolysis of 4 in CH2Cl2 at room temperature in the pre

151 alysis indicate that NO2(*) is released upon photolysis of 4, also consistent with the formation of 6

152 Continuous photolysis of 7b in the presence of ferrous ion or thiop

153 ) can be cleanly prepared via thermolysis or photolysis of [(Ar'O)2 Nb(CH3 )2 Cl] (1) (OAr'=2,6-bis(d

154 Mechanistic studies suggest that photolysis of a Ni(III) aryl chloride intermediate, gene

155 In addition, the photolysis of a non fluorinated pentanone (2-methyl-3-pe

156 The triggering event is the photolysis of a photosentive ortho-nitrobenzyl group.

157 alyst produces over 300 turnovers of H2 upon photolysis of a solution of acetonitrile, water, triflic

158 cies initiated by UV-A light may have caused photolysis of AFB(1) and AFM(1) molecules in water.

159 a novel hexacyclic ring system following the photolysis of altrenogest (1).

160 Here, it is reported that direct photolysis of altrenogest under environmentally relevant

161 rivatives was achieved by solvent controlled photolysis of appropriate 2-nitrobenzyl alcohols.

162 n this report, we describe the visible light photolysis of aryl diazoacetates in the presence of some

163 UV-mediated photolysis of azF was then carried out to induce targete

164 have so far proven impossible to isolate by photolysis of azides.

165 Results show minimal hydrolysis and photolysis of BPA over 55 days, confirming its persisten

166 ed with amperometry and stimulation by flash photolysis of caged Ca(2+).

167 sitol 1,4,5-trisphosphate (IP3) receptors by photolysis of caged IP3 The rate of Ca(2+) removal from

168 The 193-nm photolysis of CH(2)CHCN illustrates the capability of ch

169 SWCNT sidewalls with oxygen atoms formed by photolysis of ClO(-) ions.

170 Photolysis of compound 2 results in the formation of CAA

171 Here, we investigated the photolysis of dichloroacetamide safeners to better under

172 Biodegradation and photolysis of dissolved organic matter (DOM) in boreal h

173 Photolysis of E(4)(4H) causes hydride-re with release of

174 (4)(H(2),2H) has not been trapped, cryogenic photolysis of E(4)(4H) provides a means to address this

175 ation process, we carried out in situ 450 nm photolysis of E4(4H) in an EPR cavity at temperatures be

176 excess nutrients, but its ability to enhance photolysis of emerging contaminants has not been evaluat

177 Photolysis of ethyl 3-azido-4,6-difluorobenzoate at room

178 the acute toxicity of EDDS increased as the photolysis of Fe(III)EDDS proceeded.

179 ange of the NTA toxicity occurred during the photolysis of Fe(III)NTA; however, the acute toxicity of

180 to initiate reactions (NOx photo-oxidation, photolysis of H2O2, ozonolysis, or thermal decomposition

181 The efficient gas-phase photolysis of Hg(II) and Hg(I) has recently been reporte

182 However, whether the photolysis of Hg(II) leads to other stable Hg(II) specie

183 behavior of Hg(I) radicals and show that the photolysis of HgBr increases atmospheric mercury lifetim

184 Here we studied photolysis of HNO(3) on Pyrex glass in a photochemical f

185 ntum yields for radical generation by the UV photolysis of HOCl, OCl(-), and NH2Cl of 0.62, 0.55, and

186 gh the hydroxyl radical ((*)OH) generated by photolysis of hydrogen peroxide (H(2)O(2)) is most commo

187 nerates these radicals through laser-induced photolysis of hydrogen peroxide.

188 OFR applications using only photolysis of injected O(3) to generate OH are less pref

189 g electric field (4 x 10(7) V/cm) during the photolysis of isolated phenol (C(6)H(5)OH) molecules to

190 s of the H atoms and S((1)D) atoms formed by photolysis of jet-cooled H(2)S molecules at many wavelen

191 However, the photolysis of key Hg(I) species within that cycle is cur

192 In this study, we evaluated the sunlight photolysis of metolachlor and benoxacor, individually an

193 Product analysis following photolysis of N-t-butyloxycarbonyl-S,S-dibenzothiphene s

194 Overall, radicals generated from photolysis of NH(2)Cl alone achieved removal of indicato

195 (*), and Cl(*)) that were generated from the photolysis of NH(2)Cl and NHCl(2) at different wavelengt

196 Cl(*), and Cl(2)(-*)) than NH(2)Cl, while UV photolysis of NH(2)Cl at 255 nm generated higher concent

197 UV photolysis of NHCl(2) at 265, 285, and 300 nm generated

198 Photolysis of nitrate (NO3(-)) produces reactive nitroge

199 Indoor photolysis of nitrous acid (HONO) generates hydroxyl rad

200 predict indoor HOx production rates from the photolysis of nitrous acid (HONO), hydrogen peroxide (H2

201 h the photooxidation of ferrous ions and the photolysis of organic thiols.

202 boratory experiments further demonstrate the photolysis of particulate nitrate collected on filters a

203 ently discovered NOx recycling route, namely photolysis of particulate nitrate, on the modeling of NO

204 assess that possibility, we investigated the photolysis of perfluoro-2-methyl-3-pentanone (PF-2M3P),

205 The photolysis of PF-2M3P and PF-3M2B was found to have a mi

206 The photolysis of phenylphosphirane in (3)P-O2 doped matrice

207 The 266 nm laser flash photolysis of phtaloyl peroxide (2) in liquid acetonitri

208 (or NO2(+)) generated from the UV photolysis of RDX, HMX (or PETN).

209 Photolysis of SAE bound to HydG forms an ethyl radical t

210 The use of laser-triggered photolysis of silver trifluoroacetate to generate triflu

211 Macrophyte removal enhanced photolysis of some compounds (e.g., hydrochlorothiazide

212 oether attached at the meso-position undergo photolysis of the [C-S] bond under green light (lambda=5

213 Room temperature photolysis of the bis(azide)cobaltate(II) complex [Na(TH

214 of the centrosomal Ca(2+) signals, by flash photolysis of the caged Ca(2+) chelator diazo-2-acetoxym

215 s) of the Cu(B)(+)-CO complex generated upon photolysis of the CO-bound mixed-valence Tt ba(3) (Kouts

216 Fe(III/II)NTA and Fe(III/II)EDDS and the UV photolysis of the complexes in Milli-Q water and OSPW we

217 The photolysis of the Fe(III)-Pyo complex leads to the gener

218 g attempted photochemical unmasking, whereas photolysis of the indane rotaxane results in unmasking o

219 Subsequent photolysis of the intermediate A results in HNO producti

220 No electron backflow was detected after photolysis of the mixed-valence CO-bound Tt ba(3).

221 cts were detected upon experimental sunlight photolysis of the pharmaceutical carbamazepine (CBZ) in

222 We simulated photolysis of the pharmaceuticals morphine, codeine, and

223 (17-19); OR(f) = perfluoro-tert-butoxy) via photolysis of the precursor complex [(HEB)Re(CO)3][Al(OR

224 Direct photolysis of the substrates with UV-A light centered at

225 carbonylnitrene have been observed following photolysis of these sulfilimine precursors by time-resol

226 Photolysis of trenbolone acetate (TBA) metabolites in th

227 The photolysis of triethylamine (1a) in the presence of carb

228 investigate the wavelength-dependence of the photolysis of two inorganic chloramines (NH(2)Cl and NHC

229 d polarization of a MgO (111) support during photolysis of water at elevated temperatures.

230 gation of the effects of direct and indirect photolysis on citric and malic acid-based CDs.

231 The impact of chlorine photolysis on dissolved organic matter (DOM) composition

232 t receptors compared to IMD, suggesting that photolysis on environmental surfaces increases toxicity.

233 leaves to determine the potential impact of photolysis on the phytoremediation of contaminants.

234 ntally observable, for example, under matrix photolysis or flash vacuum pyrolysis conditions.

235 roducts that were not detected during direct photolysis or reaction with .OH.

236 adical (.OH) produced by nitrate and nitrite photolysis oxidizes contaminants, absorption of light al

237 ivities, with NO and isoprene emissions, NO2 photolysis, ozone BCs, and deposition velocity being amo

238 (*), and CO(3)(*)(-)) generated from nitrate photolysis partially oxidized formate to highly reductiv

239 ter effluent, nitrate and nitrite-sensitized photolysis pathways resulted in production of transforma

240 Light irradiation leads to their photolysis, producing radicals.

241 Analysis of surface-bound IMD photolysis products was performed using attenuated total

242 Finally, CPA photolysis products were isolated by semi-preparative hi

243 The photolysis quantum yield of the virus outweighed the sea

244 T to a Ca(2+) chelator that upon laser flash photolysis rapidly releases Ca(2+) in <0.2 ms.

245 Organic compounds further enhance the photolysis rate constant by up to one order of magnitude

246 The photolysis rate constant of HNO(3(s)) varied with D(HNO3

247 Photolysis rate constant of HNO(3) on the surface (HNO(3

248 orption profiles alter important atmospheric photolysis rate constants [e.g., J(NO2) and J(O3)] by at

249 Despite the large AQY variability, daily photolysis rate constants at the sea surface spanned a s

250 We also calculated photolysis rate constants for nitrogen dioxide (NO2) and

251 The photolysis rate of benoxacor depended on its initial sur

252 otolysis in future models for O3 and for the photolysis rate of particulate nitrate to be quantified

253 oud scenario, the integrated ClNO(2) and ICl photolysis rates are 3.7 x 10(7) and 3.1 x 10(7) molecul

254 ree scenario, the integrated ClNO(2) and ICl photolysis rates are 8.1 x 10(7) and 3.6 x 10(7) molecul

255 ozonation leads to an enhancement of direct photolysis rates due to the increased transparency of th

256 or regional or large-scale assessment of DMS photolysis rates in future studies.

257 We incorporate our photolysis rates into a regional chemical transport mode

258 solved nitrogen was mainly controlled by the photolysis rates of nitrate and nitrite.

259 important insights into the mechanism of the photolysis reaction.

260 Results of photolysis reactions and computational chemistry complem

261 used the numerical model MIKE-21 to simulate photolysis reactions within the inundated surface water

262 est the occurrence of photofragmentation (or photolysis) reactions.

263 Several glyoxal loss processes such as photolysis, reactions with hydroxyl radicals, and aeroso

264 found it to exhibit a faster rate toward UV photolysis relative to simple nitroveratryl-based protec

265 ) to study the effect of direct and indirect photolysis, respectively.

266 Preliminary photolysis studies with green light have demonstrated th

267 rmation was observed during the iron-complex photolysis, suggesting that fragmentation can occur afte

268 Mechanistic studies using laser flash photolysis, supported by quantum mechanical calculations

269 The developed loose patch photolysis technique can provide striking new insights i

270 Using a laser-pulse photolysis technique, combined with whole-cell recording

271 Using a laser-pulse photolysis technique, we investigated the effect of gamm

272 ed wood tar aerosols are more susceptible to photolysis than to OH(*) reactions.

273 ther unreactive with respect to direct solar photolysis, they photoreacted in the presence of H2O2, f

274 has been obtained by nanosecond laser flash photolysis through detection of long-lived transients.

275 nalog oxidation were obtained by laser flash photolysis through direct observation of (3)sens* and ra

276 e the total excitation volume and, thus, the photolysis time.

277 in without the need for polymers, by linking photolysis to an isoelectric point shift, which itself i

278 3+) bridging dinitrogen complex to UV-light, photolysis to form the monomeric Sc(2+) complex, [K(cryp

279 Chlorine photolysis transforms DOM through multiple mechanisms to

280 The CO photolysis triggers a large-scale migration of the subst

281 de safeners, only benoxacor undergoes direct photolysis under simulated natural sunlight ( t(1/2) ~ 1

282 y fate of IONO(2) is believed to be, besides photolysis, uptake by aerosol surfaces, leading to parti

283 A range of methods including oxidation, photolysis, UV-degradation, nanofiltration, reverse osmo

284 s that apparent quantum yields (AQY) for DMS photolysis varied according to the quantity and quality

285 methylcyanoacetylene and MeC5N by gas-phase photolysis was evaluated from relevant acetylene derivat

286 Direct photolysis was the dominant transformation mechanism for

287 ir was introduced in both chambers, and HONO photolysis was used to produce hydroxyl radicals (OH) in

288 ith O(3), hydroxyl radicals (OH), and due to photolysis were calculated.

289 owed by the photochemical OH(*) reaction and photolysis were investigated in tandem flow reactors.

290 g, a small-molecule dimerizer that undergoes photolysis when exposed to blue light.

291 Such processes are divided into direct photolysis, where a molecule is transformed following su

292 ts were increased markedly by mercury arc UV photolysis, which covers the zinc atomic absorption.

293 a paucity of laboratory measurements of SOA photolysis, which limits how well photolytic losses can

294 OH(X) radicals from vacuum ultraviolet water photolysis, which may be related to the production of th

295 formation of dA* was followed by laser flash photolysis, which yields a transient with lambdamax appr

296 photonic platforms to be used for asymmetric photolysis with lower energy requirements.

297 (O(t)Bu)(3))(4)(N)], 3, can be prepared upon photolysis with UV light of the U(IV) azide analogue.

298 ors at concentrations that are effective for photolysis with violet light.

299 C(+)-(4-MeO-C6H4)] (generated by laser flash photolysis) with diverse nucleophiles (e.g., pyrroles, h

300 Optimal restored floodplain conditions for photolysis would maximize light exposure, which may diff