Reactions of Microsolvated Organic Compounds at Ambient Surfaces: Droplet Velocity, Charge State, and Solvent Effects
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The exposure of charged microdroplets containing organic ions to solid-phase reagents at ambient surfaces results in heterogeneous ion/surface reactions. The electrosprayed droplets were driven pneumatically in ambient air and then electrically directed onto a surface coated with reagent. Using this reactive soft landing approach, acid-catalyzed Girard condensation was achieved at an ambient surface by directing droplets containing Girard T ions onto a dry keto-steroid. The charged droplet/surface reaction was much more efficient than the corresponding bulk solution-phase reaction performed on the same scale. The increase in product yield is ascribed to solvent evaporation, which causes moderate pH values in the starting droplet to reach extreme values and increases reagent concentrations. Comparisons are made with an experiment in which the droplets were pneumatically accelerated onto the ambient surface (reactive desorption electrospray ionization, DESI). The same reaction products were observed but differences in spatial distribution were seen associated with the “splash” of the high velocity DESI droplets. In a third type of experiment, the reactions of charged droplets with vapor phase reagents were examined by allowing electrosprayed droplets containing a reagent to intercept the headspace vapor of an analyte. Deposition onto a collector surface and mass analysis showed that samples in the vapor phase were captured by the electrospray droplets, and that instantaneous derivatization of the captured sample is possible in the open air. The systems examined under this condition included the derivatization of cortisone vapor with Girard T and that of 4-phenylpyridine N-oxide and 2-phenylacetophenone vapors with ethanolamine.
Key wordsMicrosolvated compounds Ion/surface reactions Solvent effects Mass spectrometry Charged droplets Desorption electrospray ionization Ion soft landing
Microsolvated compounds represent an important class of chemical entities in nature; they exist in the earth’s polar stratosphere as well as in many biological systems. Stratospheric cloud surfaces [nitric acid trihydrate (type I) and water-ice (type II)] are considered important reaction sites in atmospheric science [1, 2], and the possible significance of charged reagents in such reactions as atmospheric condensation and ice nucleation have been discussed . For example, formation of nitric acid from N2O5 on ice surfaces is thought to involve microsolvated species [4, 5, 6, 7, 8], which include protonated water clusters [5, 6]. In biochemistry, hydrophobic pockets of proteins are known to contain fewer solvent molecules than the rest of the bulk protein. Transport of ions through membranes mediated by proteins  also requires that the ion shed some of its solvent molecules ; the type of ion (Na+ or K+) transported through a particular ion channel thus depends strongly on the hydration energy of the ion . Unfortunately, studies involving microsolvated organic molecules are limited [12, 13], especially as reagents in chemical reactions under atmospheric pressure conditions. Microsolvated peptide ions have been studied in vacuum by Williams and coworkers [14, 15], where the effects of solvation on reactivity are clearly linked to changes in thermochemical properties. Herein, we investigate the reactivity of simple organic ions at ambient surfaces in the presence of small quantities of solvent. The selected reactions have characteristic pathways under bulk solution-phase conditions, and the general goal of this study was to examine the reactivity—including possible new pathways—of the microsolvated species in the open air, and to interpret the results in the light of solvent effects.
Experimental [16, 17, 18, 19] and theoretical  studies on gas-phase ion/molecule reactions of microsolvated ions have included the investigation of solvent effects [21, 22]. The experimentally observed trend is a reduction in the reaction efficiency, which starts with monosolvation. Searles and Kebarle made some of the first detailed observations of the effects of solvation on alkali cations (M), and observed an increase in the enthalpy of formation of hydrated species in the series M(H2O) n + where n ranges from n = 1 upwards [23, 24]. Theoretical investigations reveal a systematic transformation of the gas-phase double-well potential to an energy profile for nucleophilic substitution with much shallower reactant and product complex minima and an increased activation barrier upon successive hydration [16, 25, 26]. Thus, the energy profiles of gas-phase microsolvated ion/molecule reactions approach those for bulk solution-phase reactions (except for a few instances ), in which large activation energies are typically required.
Interestingly, increased reaction rates have been observed for certain solution-phase reactions conducted under microreactor conditions, in which the presence of microsolvated species cannot be ruled out. Such microreactor systems have larger surface areas, which affect physical processes, such as evaporation, and support partitioning of solutes from the droplet bulk to droplet surface [27, 28, 29]. Examples of such microreactor systems include the creation of gas/vapor-phase bubbles in liquids by ultrasonication [30, 31] as well as the recent observations of accelerated reactions in charged microdroplets by reactive desorption electrospray ionization (reactive DESI ). Aside from the accelerated reaction rates, the DESI methodology has also been shown to be efficient in capturing transient reaction intermediates in bulk solution-phase on millisecond time scale . In sonochemistry, acoustic cavitation causes the formation, growth, and implosive collapse of bubbles in a liquid, releasing large amounts of heat (5000 °C within lifetimes of a few microseconds) that increase rates of chemical reaction by several orders of magnitude. In reactive DESI experiments by contrast, smaller droplets generated upon evaporative cooling of solution-phase charged microdroplets are thought to increase the rates of acid/base catalyzed solution-phase bimolecular reactions . To the best of our knowledge, heterogeneous surface reactions utilizing charged microdroplets have not been reported, although heterogeneous gas-phase ion/surface reactions under vacuum are common [34, 35].
The instrumentation used for the vacuum-base ion/surface reactions is based on the ion soft landing (SL) technique [36, 37, 38] in which mass-selected polyatomic ions are deposited intact onto a surface using a mass spectrometer. For surface reactions, the selected ion is given enough energy to react selectively with particular functional groups present at the surface. Recently, the SL technique was extended from vacuum to ambient conditions in a process termed ambient soft landing . In ambient ion soft landing, polyatomic organic ions are deposited from air onto a surface at a specified location under atmospheric pressure conditions. The present work utilized the ambient soft landing apparatus except that charged microdroplets, instead of dry ions, were selected for deposition and reaction at an ambient surface.
Three different experimental conditions are utilized in this study on the Girard condensation as the test reaction: (1) ambient reactive soft landing utilizing slow velocity droplets, (2) reactive DESI in which high velocity droplets are used , and (3) vapor phase analyte capture and reaction in charged microdroplets. The charged droplets used in this study were generated using electrosonic spray ionization (ESSI ) because it allows transport of the electrosprayed droplets over a greater distance. The advantage of this type of electrospray (ESI [29, 42, 43]) is that it allows some solvent evaporation from the droplets during their transfer to the designated location, and the use of the derived charged microdroplets for surface reactions at atmospheric pressure. To effect surface reaction, the charged microdroplets containing the desired reagent ion were directed onto the reaction surface containing a nominally dry reagent using the ambient soft landing apparatus [39, 44]. Under particular experimental conditions (discussed later), this apparatus allows focusing of the ions onto a 2 mm (diameter) spot size, producing no observable macroscopic solvent on the surface. Ion/surface reactions were achieved upon interaction of the microdroplets with the reagent already present at the surface. Results indicated increased product yields for the surface reaction compared with the corresponding bulk solution-phase reactions, and possible factors influencing the observed rate enhancement are discussed. The vapor-phase analyte capture experiment was achieved by modifying the ambient soft landing apparatus to allow charged droplets doped with a reagent to intercept the headspace vapor of an analyte (after being heated) in an enclosed chamber. Vapor-phase analytes, which are captured by the charged droplets, are then directed onto a surface for collection and characterization. Removal of the deposited material and analysis by MS showed that reaction of the captured analyte with reagents contained in charged droplets is possible in the open laboratory [45, 46, 47, 48]. As will be shown, the charged droplet environment (either at a surface or in air) provides the required conditions in which solvated organic ions can be utilized effectively for acid catalyzed reactions.
2.2 Nanospray Ionization Mass Spectrometry for Product Analysis
After surface reaction, the spots on which ions had impinged were washed with 10 μL of methanol/water (1:1, vol/vol) and characterized using nanospray-MS. Nanospray (~20 nL/min flow rate) voltage of 1.8 kV was supplied to the emitter. These sample analysis conditions involve small droplets and short ionization periods; no significant reaction is observed during analysis as shown by the control experiments. All MS experiments were performed using a Thermo Fisher Scientific LTQ mass spectrometer (San Jose, CA, USA). Typical MS parameters used included averaging of 3 microscans, 100 ms maximum ion injection time, 15 V capillary voltages, 150 °C capillary temperature, and 65 V tube lens voltage. Data were acquired and processed using Xcalibur 2.0 software (Thermo Fisher Scientific). The identification of analyte ions was confirmed by tandem mass spectrometry using collision-induced dissociation (CID). An isolation window of 1.5 Th (mass/charge units) and a normalized collision energy of 30%–35% (manufacturer’s unit) was selected for the CID experiment.
2.3 Chemicals and Reagents
Cortisone, androsterone, testosterone, Girard T reagent, and 4-phenylpyridine N-oxide were purchased from Sigma-Aldrich (Milwaukee, WI, USA), whereas ethanolamine was obtained from Acros Organics (Geel, Belgium), and methanol and acetonitrile (HPLC grade) from Mallinckrodt Baker Inc. (Phillipsburg, NJ, USA). Deionized/distilled water was obtained using a Barnstead/Thermolyne deionizer unit (Barnstead Mega-Pure System, Dubuque, IA, USA).
3 Results and Discussion
3.1 Charged Droplet/Surface Reactions
Two main factors have been identified as influencing the increased reaction rate observed for the GT reaction with the ketones at the surface, the effects of charge and solvent. Charge effects were investigated by supplying +7, –7, and 0 kV voltages independently to the GT spray solution and directing the derived electrosprayed droplets onto the reaction surface containing dried cortisone. The results indicated that more reaction product (m/z 474) was collected for +7 kV spray voltage, followed by –7 kV (Figure S3, Supporting Information). This result is not surprising because the GT reaction with ketone is acid catalyzed and, in fact, the pH of the landing positively charged microdroplets (after traveling a distance of 12 cm) generated by the +7 kV spray voltage was measured to be 1.5, whereas the pH of landing negatively charged droplets (generated using –7 kV spray voltage) was found to be 2.5. The poor performance observed when no voltage was supplied to the spray solution is attributed to fewer GT reagents at the reaction surface and insufficient pH modification due to the lack of charge in the landing microdroplets (pH could not be measured possibly because the droplets are too small). The pH of the droplets immediately after exiting ESI source was measured to be 3.5 (positive droplets) and 4.0 (negative droplets). No product ion (m/z 474) was observed when the GT was prepared in a solution of pH 10. The pH of the landing droplets was 12.5 in this case for negatively charged droplets. Aside from charge polarity (i.e., positive versus negative droplets), the type of ions (protonated versus sodiated, etc.) contained inside the charged microdroplets was also found to affect reaction efficiency. For example, a large reduction in reaction yield was observed when the keto-steroid (e.g., androsterone) solution in acetonitrile was electrosprayed, and the resulting positively charged microdroplets were allowed to interact with dried GT present at the surface (Figure S4, Supporting Information). In this reverse experiment (spraying the keto-steroid instead of GT), the charged droplets were determined to contain sodiated/potassiated dimers and trimers of the keto-steroid, with no or little protonated monomeric species. Since the GT reaction with ketone is acid catalyzed, the protonated ketone can be considered more reactive than the sodiated or potassiated species (Figure S5, Supporting Information), and so the absence of such protonated species should ultimately result in reduction in the reaction efficiency.
It seems likely that solvent evaporation from the microdroplets will ultimately lead to microsolvation of reagents during (1) transfer to the reaction surface, and/or (2) during residence time on the surface. Thus, the effect of solvent evaporation on reaction rate was investigated by performing a delayed dissolution experiment using the Girard T and cortisone reaction system. That is, following reagent deposition, the reaction mixture was either kept in the open air or under a dry environment inside a dessiccator, for a given time before washing. The open-air condition showed a modest 2-fold increase in product yield as a function of delay time (time over which the reaction mixture was kept before dissolving it into solution for MS analysis), within a 30 min delay time (Figure S6a, Supporting Information). In the dry environment, however, no significant increase in reaction yield was observed irrespective of the delay time. These results indicate that evaporation of the microscopic amounts of solvent present at the surface led to a significant increase in reaction yield, even after droplet deposition had ceased. This effect was further investigated simply by pipetting 2 μL each of the GT (50 ppm) and cortisone (100 ppm) solutions in acetonitrile onto a surface in the open air. The resulting dried reaction mixture was dissolved in 10 μL of methanol/water (1:1, vol/vol) solution and analyzed using nanospray-MS. The results of this experiment also showed that the longer the reaction mixture was allowed to stand in the open air, the more product was collected (red trace, Figure S6b, Supporting Information), hence confirming the effect of evaporation on reaction yield. Again, due to the combined effects of charge and solvent evaporation, more products were collected for charged microdroplets than from the neutral droplets derived from drop-casting.
3.2 Charged Droplet/Vapor Capture and Reaction
The reactivity of organic ions has been studied at atmospheric pressure under two different experimental conditions: (1) using reactive soft landing and (2) using vapor-phase capture by charged droplets, and comparisons have been made with a third experiment (3) reactive DESI. The reactions of interest include cortisone reaction with Girard T reagent and ethanolamine reaction with 4-phenylpyridine N-oxide and with 2-phenylacetophenone. More than an order of magnitude increase in product yield was observed for the charged droplet/surface reaction compared with the corresponding bulk solution-phase reactions performed using the same amounts of material. Electrospray appears to provide an efficient way to generate highly reactive microsolvated organic ions in the form of charged microdroplets in ambient air. Ambient ion soft landing allows ions and charged droplets to be effectively transported, focused, and deposited gently at a designated location for reaction with a chosen reagent. While most reactive species are expected to be the fully desolvated ions, these might be more difficult to deal with in quantity, so the conditions and rate enhancements seen here are associated with partial (and poorly characterized) degrees of desolvation. Unlike ambient reactive DESI experiments in which rate enhancements are also seen, the procedures used in this work do not involve fast-moving droplets so they do not generate splashes upon surface impact of the primary droplets. Reactions are limited to those that occur at the impact site. The observed rate enhancements associated with this reactive soft landing are ascribed to both charge and solvent effects. The use of charged droplets allows extremes of pH to be reached in the droplet arriving at the impact point while solvent evaporation also provides increased reagent concentration. Both factors allow the reaction to approach those used in isolated-phase ion/molecule reactions, which often occur upon every collision.
Charged microdroplets also served as reaction vessels to capture gas-phase analytes—a known process —and to follow this with previously unknown reaction. This sequence enabled direct capture of gas-phase analyte in ambient air, followed by their reaction and then transfer of the derivatized product onto a surface for collection and independent characterization.
The authors acknowledge funding for this work by the National Science Foundation (CHE NSF 0848650).
- 9.Hille, B.: Ion channels of excitable membranes, 3rd edn. Sinauer Associates, Sunderland (2001)Google Scholar
- 10.Stryer, L.: Biochemistry, 3rd edn. W.H. Freeman and Company, New York (1988)Google Scholar
- 17.van der Wel, H., Nibbering, N.M.M., Sheldon, J.C., Hayes, R.N., Bowie, J.H.: Nucleophilic substitution in the gas phase. The reactions of alkoxide-alkanol negative ions with boron, carbon, silicon, and titanium alkoxides. An ion cyclotron resonance and ab initio study. J. Am. Chem. Soc. 109, 5823 (1987)CrossRefGoogle Scholar
- 43.Cole, R.B.: Electrospray Ionization Mass Spectrometry: Fundamentals Instrumentation and Applications, 1st edn. John Wiley and Sons, New York (1997)Google Scholar
- 44.Badu-Tawiah, A.K., Cyriac, J., Cooks, R.G.: Reactions of organic ions at ambient surfaces in a solvent-free environment. J. Am. Soc. Mass Spectrom. (2012). doi: 10.1007/s13361-012-0337-7
- 45.Fuerstenau, S., Kiselev, P., Fenn, J.B.: ESIMS in the analysis of trace species in gases. Proceedings of the 47th ASMS Conference on Mass Spectrometry Allied Topics, Dallas, TX, June, (1999)Google Scholar
- 46.Kiselev, P., Fenn, J.B.: ESIMS Analysis of Vapors at Trace Levels. Proceedings of the 49th ASMS Conference on Mass Spectrometry and Allied Topics, Chicago, IL, May, (2001)Google Scholar