ライフサイエンスコーパス: photolysis

1 sence of light is observed after the initial photolysis.

2 y biphasic Ca(2+) transients following light photolysis.

3 uct (a 4-methylcoumarin-3-yl thioether) upon photolysis.

4 triplet excited states (T1), by laser flash photolysis.

5 Notably, Ru2(chp)4Cl (3) is recovered after photolysis.

6 data with absolute kinetics from laser flash photolysis.

7 ylacetamide (DMA) was studied by laser flash photolysis.

8 e methides (QMs) was observed by laser flash photolysis.

9 dical (CumO(*)) were measured by laser flash photolysis.

10 dical (CumO(*)) were measured by laser flash photolysis.

11 re detected and characterized by laser flash photolysis.

12 ently observed if the nitrene is produced by photolysis.

13 ntify contributions from direct and indirect photolysis.

14 th-abundant materials for water electrolysis/photolysis.

15 age on the ketone moiety and self-sensitized photolysis.

16 tivation of porphyrin molecules and particle photolysis.

17 uran/n-hexane, n-hexane, or methanol) during photolysis.

18 te-photocycle intermediates studied by flash photolysis.

19 y separated from the reaction solution after photolysis.

20 eliminated using chromophore-targeted laser photolysis.

21 roteins could subsequently be deprotected by photolysis.

22 were rapidly photoenhanced, followed by slow photolysis.

23 on intermediates, were investigated by flash photolysis.

24 arine boundary layer via particulate nitrate photolysis.

25 as volcanic sulfate aerosols formed from OCS photolysis.

26 Photolysis (380 nm) of trans-Pt(PEt3)2(Cl)(OH)(OOH)(4-tr

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

28 Loose patch photolysis allows the measurement of transmembrane ionic

29 We initiated SOA aging with UV photolysis alone and with OH radicals in the presence or

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

31 rmally, e.g., under the conditions of matrix photolysis and flash vacuum thermolysis.

32 adation within the UV/H2O2 AOP via UV direct photolysis and hydroxyl radical ((*)OH) reaction, so tha

33 etics and pathways in surface waters (direct photolysis and indirect photoreactions) were studied for

34 of the octa- and nona-BDE profiles suggested photolysis and pyrolytic debromination of BDE-209 in the

35 2 production mechanisms in comets, including photolysis and radiolysis of water, solar wind-surface i

36 Both direct photolysis and reaction with (3)DOM form Trp radical cat

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

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

39 n this work, a combined investigation of the photolysis and temperature-dependent OH radical reaction

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

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

42 le mechanistic studies including laser flash photolysis and time-resolved fluorescence, we demonstrat

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

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

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

46 abilizing indole radical cations formed upon photolysis, and prevents their deactivation by reaction

47 escence measurements, nanosecond laser flash photolysis, and quantum chemical calculations.

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

49 died by steady state photolysis, laser flash photolysis, and theoretical calculations.

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

51 Reaction with singlet oxygen and direct photolysis are secondary processes that are both still m

52 rbonyl (oxygenated VOCs with a C = O moiety) photolysis as a dominant oxidant source.

53 he temperature dependence of p-benzoquionone photolysis as a model compound for DOM and observed no t

54 The photolysis at 222 nm of 5-methyltetrazole isolated in a

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

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

57 Experimental results of N2 photolysis at vacuum UV wavelengths in the presence of h

58 and and -3.0 +/- 0.2 per thousand for direct photolysis, at pH 7.4 and pH 5, respectively.

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

60 the [2+2+2] cycloaddition are assisted by UV photolysis, but strict photocontrolled methods are unatt

61 the production of OH radicals through ozone photolysis by UV and visible light at the air-water inte

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

63 the dark but rapidly under illumination, and photolysis can also produce doubly reduced 1,4,5,6-tetra

64 Because photolysis can be performed on fast time scales and at l

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

66 ggested a substantial overestimation in HONO photolysis contribution to hydroxyl radical budget.

67 onate, pyruvate, and oxalate, with a complex photolysis contribution to overall degradation of 46, 40

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

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

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

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

72 ot a good metric for assessing the extent of photolysis-driven aging in NAP SOA (and in BrC in genera

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

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

75 N = -7.3 per thousand +/- 0.3 per thousand), photolysis (epsilonN = +1.9 per thousand +/- 0.1 per tho

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

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

78 Photolysis experiments (in H2O and D2O) and quantum chem

79 Low-temperature photolysis experiments (T = 10 K) on the tripodal azido

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

81 ble and infrared spectral range and by flash-photolysis experiments on the longer time scale.

82 The steady-state photolysis experiments showed for the investigated sulfi

83 Flash-photolysis experiments showed overall fast biphasic CO r

84 Steady-state photolysis experiments showed the prevailing formation o

85 was unequivocally established by laser flash photolysis experiments showing the absorption bands of 3

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

87 Low-temperature FTIR photolysis experiments with 1a in acetonitrile do not re

88 re identified and quantified by steady-state photolysis experiments, laser spectroscopy and kinetic m

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

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

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

92 with recent measurements using diiodomethane photolysis for CH2OO generation.

93 ived species, meteorological parameters, and photolysis frequencies.

94 ch probes active site dynamics after hydride photolysis from Nia-C, indicates the E17Q mutation does

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

96 to enhance spinogenesis induced by glutamate photolysis in both dSPNs and iSPNs, suggesting that iSPN

97 ical (BONO)), was carried out by laser flash photolysis in CH3CN.

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

99 ile does not yield any new products, whereas photolysis in oxygen-saturated acetonitrile yields benza

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

101 pentafluoropyridine) employing in situ laser photolysis in the NMR probe, resulting in a wide-ranging

102 ved AAs is well investigated, their indirect photolysis in the presence of chromophoric dissolved org

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

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

105 Photolysis is a major removal pathway for the biogenic g

106 Fe(III) complex photolysis is an important additional sink for tartronat

107 yne remains the predominant product when the photolysis is carried out in cyclohexene but the carbene

108 Photolysis is not likely an important fate for NO3 indoo

109 Photolysis (lambda > 472 nm) of 2-diazo-3-pentyne (11) a

110 degrees inverted geometry and an integrated photolysis laser, that is optimized for applications in

111 nd the mechanism was studied by steady state photolysis, laser flash photolysis, and theoretical calc

112 termined using the technique of pulsed laser photolysis-laser-induced fluorescence.

113 ent triplet state is observed in laser flash photolysis (LFP) experiments of 1, with lifetimes 1 orde

114 ethide (QM) that was detected by laser flash photolysis (LFP) in 2,2,2-trifluoroethanol (lambda = 580

115 adical cations as indicated by a laser flash photolysis (LFP) study of the photochemical oxidation of

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

117 by fluorescence spectroscopy and laser flash photolysis (LFP).

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

119 At 0 degrees SZA, a photolysis lifetime of 3-4 h has been obtained.

120 A photolysis lifetime of about 26 days was estimated with

121 A (22 +/- 5% by weight), have an atmospheric photolysis lifetime of about 6 days at a 24-h average so

122 The results show that the photolysis lifetime of MClDMS is significantly smaller t

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

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

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

126 Indeed, laser flash photolysis measurements showed an efficient formation of

127 al evidence suggests a sequential, two stage photolysis mechanism which leads to a nonlinear response

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

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

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

131 Thermal decomposition or room-temperature photolysis of 1 gives O2, water, and 2.

132 Laser flash photolysis of 1 in oxygen-saturated acetonitrile results

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

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

135 Laser flash photolysis of 1a in argon-saturated acetonitrile (lambda

136 Similarly, photolysis of 1a in the presence of bromoform allows the

137 Laser flash photolysis of 1b in acetonitrile shows a transient absor

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

139 rated by reaction of 3 with HCl or by direct photolysis of 2 in chlorobenzene.

140 the effect of the environment on the rate of photolysis of 2,4-dinitrophenol (24-DNP), an important e

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

142 The reaction involves the photolysis of 2-azidophenols to generate iminoquinone in

143 Photolysis of 2-Cl-anilinium cations exhibits normal C a

144 plet 2-formyl phenylnitrene was generated by photolysis of 2-formyl phenylazide isolated in Ar, Kr, a

145 In contrast, photolysis of 2-methyl-3-phenyl-2H-azirine (1b) in aceto

146 Matrix photolysis of 2-pyrazinyl azides/tetrazolo[1,5-a]pyrazin

147 In stark contrast to the slow photolysis of 24-DNP in an aqueous solution, the photoly

148 In contrast, the photolysis of 3-Cl-aniline was almost insensitive to C i

149 Photolysis of 3-methyl-2-phenyl-2H-azirine (1a) in argon

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 ope fractionation associated with the direct photolysis of 4-Cl-aniline used as a model compound for

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

154 benzofuran-2,3-dione (11) and also by matrix photolysis of 9, 11, and 2-diazocyclohepta-4,6-dien-1,3-

155 Ar matrix photolysis of 9T/9A at 254 nm causes ring opening to gen

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

157 (GIRK) current activation was examined using photolysis of a caged agonist, carboxynitrobenzyl-tyrosi

158 rated in single- and double-stranded RNA via photolysis of a ketone precursor.

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

160 Photolysis of a nucleosome core particle containing the

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

162 d methyl peroxy radicals are produced by the photolysis of acetone and quantified as NO2 following re

163 Photolysis of alkyl iodides in the presence of Mn2(CO)10

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

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

166 Laser flash photolysis of azide 1 in argon-saturated acetonitrile sh

167 Moreover, photolysis of caged Ca elicits an inward current of simi

168 Accordingly, we applied flash photolysis of caged Ca(2+) to activate BK channels and d

169 e were followed during activation in situ by photolysis of caged calcium using bifunctional fluoresce

170 MDA receptor, or specifically by local flash photolysis of caged glutamate.

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

172 m those determined previously for the direct photolysis of chloroanilines and offer new opportunities

173 KI-TnC-A8V(+/+) relaxed more slowly on flash photolysis of diazo-2.

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

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

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

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

178 The photolysis of four nitrosamines (N-nitrosodiphenylamine

179 ve nature of products formed from UV induced photolysis of fructose.

180 or H-abstraction by OH radicals generated by photolysis of H2O2 (Lambda = 24 +/- 2).

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

182 th inorganic and biological processes (e.g., photolysis of high-molecular-weight dissolved organic ma

183 The HONO was the major product from photolysis of HNO3/nitrate on most plant leaves, whereas

184 rface density in the low-NOx forested areas, photolysis of HNO3/nitrate on the forest canopy can be a

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

186 The photolysis of HONO yields peak OH concentration values,

187 8 x 10(6) cm(-3) that were attributed to the photolysis of HONO.

188 Photolysis of matrix-isolated 1 at 254 nm also results i

189 The extra SO2 arises from photolysis of MClDMS to give CH3S and CH2Cl, followed by

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

191 It has long been known that low-temperature photolysis of Ni-C yields distinctive EPR-active states,

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

193 ed from steady-state concentrations based on photolysis of nitrate and nitrite indicating that we do

194 Photolysis of nitric acid and nitrate (HNO3/nitrate) was

195 upled to a microfluidic sensor to facilitate photolysis of nitrosothiols (i.e., S-nitrosoglutathione,

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

197 Photolysis of NO3(-) leads to NO2 and HONO, both of whic

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

199 Atmospheric direct sources of OH include the photolysis of ozone and nitrous acid (HONO) and the ozon

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

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

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

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

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

205 d by SO4(*-) radical anions derived from the photolysis of S2O8(2-) anions by 308 nm laser pulses.

206 The direct photolysis of SAL and NAR occurred via cleavage on the k

207 Photolysis of tetrazolo[1,5-a]pyrimidines/2-azidopyridmi

208 ranscription and, thus, gene expression, via photolysis of the caging groups.

209 The desired diradicals were formed upon photolysis of the chosen aromatic in aqueous phosphate b

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

211 Photolysis of the cyclic phosphine oligomer [PPh]5 in th

212 Flash photolysis of the Cys-RSE formed from Fe(II)/NO/cysteine

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

214 s in the carbonmonoxy myoglobin complex upon photolysis of the Fe-CO bond.

215 While photolysis of the latter resulted in formation of a rare

216 In contrast, photolysis of the mononuclear-DNIC species Cys-DNIC form

217 UV photolysis of the nitridoosmate(VIII) anion, OsO3 N(-) ,

218 Photolysis of the Os(II) nitrosyl product with visible w

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

220 (17-19); OR(f) = perfluoro-tert-butoxy) via photolysis of the precursor complex [(HEB)Re(CO)3][Al(OR

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

222 Photolysis of the tetrazoles/azides 8T/8A in Ar matrix g

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

224 mer, and we present (1)H NMR analysis of the photolysis of this and six other mono-, di-, and triazas

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

226 The present investigation used photolysis of two caged opioid ligands to examine the ki

227 Sunlight photolysis of uranyl nitrate and uranyl acetate solution

228 Photolysis of vinylazide 1, which has a built-in acetoph

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

230 We examined the effect of photolysis on the molecular composition, mass absorption

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

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

233 Under actual sunlight, direct solar photolysis partially degraded fluorophore organic compou

234 which increase with increasing energy of the photolysis photon.

235 By contrast, photolysis proceeds from the singlet manifold.

236 mutation does not interfere with the hydride photolysis process generating known intermediates Nia-I(

237 ective was to evaluate the importance of the photolysis process relative to OH oxidation in the atmos

238 lol molecule were generated by a nontargeted photolysis process.

239 that DOM plays an important role in indirect photolysis processes in ice, producing ROS and leading t

240 Our experiments were designed to model photolysis processes of NAP SOA compounds dissolved in c

241 esence of UV, indicating oxidative nature of photolysis products of fructose.

242 entified and may result from the reaction of photolysis products of nitrate with (photolysis products

243 tion of photolysis products of nitrate with (photolysis products of) natural organic material (NOM).

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

245 urine samples containing riboflavin and its photolysis products were successfully separated and foun

246 uding free radicals and not one of the final photolysis products, furan, were responsible for fluores

247 d following the observation of acetone among photolysis products.

248 nditions as a result of the loss of volatile photolysis products.

249 The photolysis quantum yield is temperature invariant at liq

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

251 In this work, the photolysis rate coefficient of CH3SCH2Cl (MClDMS) in the

252 00 cm(-1) region have been used to determine photolysis rate coefficients of MClDMS in the tropospher

253 The photolysis rate constant (JHNO3(s)) of the surface HNO3/

254 halonitromethanes and haloacetamides, direct photolysis rate constants (254 nm) varied by approximate

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

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

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

258 olysis of 24-DNP in an aqueous solution, the photolysis rate is increased by more than an order of ma

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

260 Photolysis rates (observed rate constant kobs = 2.7 +/-

261 lable chemistries and exhibit remarkably low photolysis rates at tunable wavelengths over a large ran

262 ation products of amines reduced nitrosamine photolysis rates by competing for photons.

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

264 eans less erythema, plant damage, and slower photolysis rates.

265 Results of photolysis reactions and computational chemistry complem

266 with several new Fe(III)-carboxylate complex photolysis reactions.

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

268 The combination of biotransformation and photolysis resulted in overall transformation rates that

269 In addition, loose patch photolysis revealed that the influx of Ca(2+) through L-

270 Laser flash photolysis showed that reaction of phenylchlorocarbene +

271 ies and, consequently, an enhancement of the photolysis sink reactions in the aerosol particles.

272 tigated by solution NMR techniques and flash photolysis spectroscopy.

273 Preliminary photolysis studies with green light have demonstrated th

274 A laser flash photolysis study on the role of solvent effects on hydro

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

276 The novel loose patch photolysis technique allowed the dissection of transmemb

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

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

279 han benzophenones and generate carbenes upon photolysis that react with a broader range of amino acid

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

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

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

283 3+) bridging dinitrogen complex to UV-light, photolysis to form the monomeric Sc(2+) complex, [K(cryp

284 ble in both complexes, which are prone to NO photolysis under visible light illumination.

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

286 Laser Flash Photolysis was employed to measure the deprotonation and

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

288 ain BR1 (ipso-hydroxylation) and upon direct photolysis was investigated.

289 Direct photolysis was the dominant transformation mechanism for

290 erved that plasma-initiated ultraviolet (UV) photolysis were responsible for the continues generation

291 nduced dissociation (CID) fragmentation, and photolysis were used to analyze SQX and its metabolites.

292 infection dose was efficient for GR activity photolysis, whereas chlorination could not appreciably a

293 ic systems to generate m-quinone methides on photolysis, which could ultimately drive the excited-sta

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

295 ht, whereas SAL and NAR could undergo direct photolysis with a high quantum yield.

296 ne and their intermediates and byproducts in photolysis with hydrogen peroxide (i.e., UV/H2O2) and va

297 rresponding Zn(2+) complex undergo efficient photolysis with quantum yields approaching 30 %.

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

299 otransformation would be dominated by direct photolysis, with half-life times of up to one month unde

300 ion of NAP SOA was significantly modified by photolysis, with the average SOA formula changing from C