Article | Open

Combining Catalytic Microparticles with Droplets Formed by Phase Coexistence: Adsorption and Activity of Natural Clays at the Aqueous/Aqueous Interface

  • Scientific Reports 7, Article number: 3215 (2017)
  • doi:10.1038/s41598-017-03033-z
  • Download Citation
Published online:


Natural clay particles have been hypothesized as catalysts on the early Earth, potentially facilitating the formation of early organic (bio) molecules. Association of clay particles with droplets formed by liquid-liquid phase separation could provide a physical mechanism for compartmentalization of inorganic catalysts in primitive protocells. Here we explore the distribution of natural clay mineral particles in poly(ethylene glycol) (PEG)/dextran (Dx) aqueous two-phase systems (ATPS). We compared the three main types of natural clay: kaolinite, montmorillonite and illite, all of which are aluminosilicates of similar composition and surface charge. The three clay types differ in particle size, crystal structure, and their accumulation at the ATPS interface and ability to stabilize droplets against coalescence. Illite and kaolinite accumulated at the aqueous/aqueous interface, stabilizing droplets against coalescence but not preventing their eventual sedimentation due to the mass of adsorbed particles. The ability of each clay-containing ATPS to catalyze reaction of o-phenylenediamine with peroxide to form 2,3-diaminophenazone was evaluated. We observed modest rate increases for this reaction in the presence of clay-containing ATPS over clay in buffer alone, with illite outperforming the other clays. These findings are encouraging because they support the potential of combining catalytic mineral particles with aqueous microcompartments to form primitive microreactors.


Clay minerals, which are composed of aluminosilicates with layered structures, are major components of soils and sedimentary rocks and among the most abundant minerals at the surface of the Earth1. Clays have found a wide variety of applications since ancient times including ceramics2, electrochemistry3, organoclay/polymer nanocomposites4 and as catalysts in chemical reactions5,6,7. The availability of clay minerals and their potential for catalytic activity led to the proposal of these materials as inorganic catalysts for chemical evolution of biomolecules on the early Earth8. Since then clay particles have been demonstrated as catalysts for polymerization of activated nucleotides and amino acids9, lipid self-organization10,11,12 and many other possible prebiotic reactions11, 13, 14.

An important step in the transition from nonliving towards living matter is thought to be compartmentalization of molecules and of reactions15, 16. Candidates for early-Earth compartments include crevices or pores in rocks17, self-assemblies of lipids or simpler amphiphiles to form vesicles18,19,20,21,22,23, and aqueous droplets formed by liquid-liquid phase separation15, 21, 24. Combining catalytic mineral surfaces with compartments such as amphiphile vesicles or droplets formed by aqueous/aqueous phase coexistence is therefore appealing as primitive protocell models. Szostak and coworkers reported that clay minerals accelerate the spontaneous conversion of fatty acid micelles into vesicles and some clay might get encapsulated within the vesicles during the process10, 12. Because the mechanism(s) of particle encapsulation within droplets of a biphasic system (partitioning and interfacial adsorption) may differ from those for amphiphile vesicles (entrapment during self-assembly), we reasoned that it might be possible to collect particles more efficiently using droplets. Here we explore the possibility of forming clay-containing or clay-coated droplets in aqueous biphasic solutions. Such structures could in principle combine compartmentalization and catalytic properties with relevance to early Earth scenarios and also potential biotechnological applications as microreactors. A possible challenge is that adsorption of polymeric solutes to the mineral surface could inhibit its catalytic activity. The immiscible aqueous phases that result upon demixing in aqueous polymer solutions provide compartments with different chemical and physical properties between which solutes such as biomolecules (or their prebiotic precursors) can partition. Consequently, aqueous two-phase systems (ATPS) have been used for biomolecule separations25, 26, food science27, 28, and biomimetic compartmentalization16, 18, 29, and have been proposed as simple protocell models15, 24, 30.

Clay microparticles can adsorb at, and stabilize, oil/water and water/air interfaces to form oil-in-water Pickering emulsions and foams31,32,33. Emulsions based on oil/water have been stabilized by clay particles34, 35 or clay particles with surfactants32 and chemical modifications36, 37. The driving force for particle assembly at these fluid interfaces is thought to be reduction of interfacial tension. The energy difference due to interfacial adsorption (ΔE) depends on the interfacial tension (γ), the particle radius (R), and the contact angle (θ). For spherical particles, the energy to remove a particle from the interface can be written as:

Δ E sphere =π R 2 γ ( 1 | cos θ | ) 2

Emulsion stabilization is generally observed when particles adsorb strongly to the interface and are preferentially wet by one of the phases, which then serves as the continuous phase38,39,40. Unmodified clays are generally hydrophilic, and consequently form oil-in-water emulsions, while hydrophobically-modified clays can stabilize water-in-oil emulsions31, 36, 39, 41. The much smaller interfacial tensions and less obvious wettability preferences at aqueous/aqueous as compared to oil/water interfaces makes stabilizing water-in-water emulsions more challenging. Nonetheless water-in-water Pickering emulsions stabilized by latex beads42, 43, protein particles44, triblock copolymers45, and synthetic clay particles40 have been produced.

Clay particles are generally nonspherical, consisting of stacked sheets, which is of interest because ΔE depends on particle shape. For thin platelet-shaped particles, the (1 | cos θ | ) term in the ΔE expression is not squared, resulting in stronger interfacial adsorption than for spheres of the same radius, except when θ = 90°38, 40. Erne and coworkers recently demonstrated stabilization of water-in-water emulsions formed from Dx 100 kDa and gelatin 100 kDa aqueous biphasic system using a synthetic clay, gibbsite, composed of aluminum hydroxide nanoplates40. Despite interfacial tension of just ~4 μN/m at their aqueous/aqueous interface, these authors were able to form stable Dx-in-gelatin and gelatin-in-Dx all-aqueous emulsions using hexagonal nanoplates only ~170 nm wide and ~7 nm thick, underscoring the favorable interfacial adsorption and reduced sensitivity to contact angle of platelet morphologies. Larger gibbsite plates also adsorbed to the Dx/gelatin aqueous/aqueous interface but due to their greater mass caused droplet sedimentation rather than the well-dispersed emulsions observed with smaller particles40.

Here, we examine the behavior of natural clay mineral particles in an ATPS formed from PEG (8 kDa) and Dx (10 kDa) (Fig. 1). A phase diagram for the PEG/Dx system is shown in Supplementary Fig. S1. We selected this system for the chemical simplicity and relatively low molecular weights of the polymers and because the PEG/Dx system has been extensively characterized15, 24, 26, 46. Although this specific ATPS is not likely to be early Earth relevant due to high total polymer concentrations, it provides an aqueous/aqueous interface with controllable interfacial tension to evaluate interfacial particle assembly and allows the impact of possible polymer-clay interactions upon particle assembly and catalytic activity to be explored. Three types of common natural clays were compared: kaolinite, montmorillonite and illite, which differ in their particle size, crystal structures and layering as well as their swelling properties. Particle distribution between the phases, polymer interactions with the particle surface, and microstructure of clay-containing biphasic aqueous systems were investigated. Despite the very similar composition and surface charge of these different clays, they behave quite differently in the PEG/Dx ATPS. Clay microparticle stabilized droplets are observed only for kaolinite and illite, both of which show adsorption of the dextran polymer to their surfaces. In contrast, montmorillonite samples did not show significant adsorption of either polymer, and were not able to form particle-coated droplets. Catalytic activities of these clay-containing ATPS were tested in a colorimetric oxidation reaction; reaction rates for clay-containing ATPS samples were similar to polymer-free controls, demonstrating that polymer binding to the clay surface did not prevent catalytic activity. Our findings suggest that natural clay microparticles can be combined with aqueous phase droplets to take advantage of both the compartmentalization capabilities of ATPS and catalytic properties of clays.

Figure 1
Figure 1

Natural clay particles catalyzing reactions in aqueous two-phase systems.

Results and Discussion

Characteristics of the natural clay minerals

Table 1 summarizes the clays studied in this work, which were selected to include the three main classes of natural clay particles: kaolinite, montmorillonite, and illite47, 48. They are all aluminosilicate minerals having layers of tetrahedrally coordinated silicon and octahedrally coordinated aluminum but differ in their number of layers, substitution ion in the layers and interlayer materials49, 50. We used two different montmorillonites to investigate the effect of exchange of different cations (Na+ and Ca2+) in clay minerals. In addition to their primary components these natural clays also contain small amounts of additional minerals as noted in Table 1.

Table 1: Charge and size measurements for clay minerals.

Despite the compositional heterogeneity of the mineral samples, all of the clay particles were negatively charged, with zeta potentials in the −30 to −45 range, consistent with their surface chemistries and with previous literature reports1, 53. Average particle size for the clays used in this work as determined by dynamic light scattering ranged between 0.48 µm to 1.58 µm (Table 1)51, 52, 54. All clay samples were polydisperse in particle size and shape, with values consistent with literature51, 52, 54, 55. Field emission scanning electron microscope (FE-SEM) images of representative particles are shown in Supplementary Figs S2 and S3. Hexagonal flake-shaped particles were observed for kaolinite and sheet-like structures for both montmorillonites (Supplementary Figs S2B,C and S3B-C). Illite consisted of small particles as shown in Supplementary Figs S2-D and S3-D.

Bulk partitioning experiments of clay particles in 15%/15% and 20%/20% w/w PEG/Dx were performed by adding clay stock solutions to ATPS with vigorous mixing, after which samples were observed over time (Supporting Figs S4 and S5). Kaolinite- and illite-containing samples showed similar partitioning to the Dx-rich phase, while the montmorillonite samples had cloudy top phases, with Na-rich montmorillonite dispersed throughout the entire sample. Different polymer concentrations only affected the Ca-rich montmorillonite, which partitioned to the PEG-rich top phase in the lower concentration ATPS, and partitioned to the Dx-rich bottom phase in the higher concentration ATPS. Sedimentation of all of the clay particles occurred over time. The observed differences in clay distribution in these bulk ATPS samples suggest that these four types of natural clays interact differently with the polymer-rich aqueous phases, which is somewhat surprising given their similar particle sizes, surface charges and aluminosilicate chemistries.

Microstructure of clay-containing ATPS

Clay particles were added to ATPS prepared from stock 15%/15% w/w PEG 8 kDa/Dx 10 kDa by mixing top and bottom phases in desired volume ratios as described in the Methods. The ATPS contained fluorescently-labeled PEG and dextran polymers to help differentiate the two phases in images (the PEG-rich phase was labeled green and the Dx-rich phase was labeled red). ATPS volume ratios 1:1 and 20:1 of PEG-rich to Dx-rich phase volumes were compared. The 1:1 volume ratio was used for simplicity and the 20:1 volume ratio was investigated because most hydrophilic molecules such as proteins, peptides, RNAs or nucleotides partition into the Dx-rich phase and hence for protocells or microreactors applications, a Dx-rich droplet phase would be desirable18, 56. Transmitted light and fluorescence micrographs for each of the four clay samples in each of the volume ratios are shown in Figs 2 and 3. An immediately striking feature of these images is the red staining of the clay particles observed most prominently for kaolinite and illite but also to a lesser extent for the two montmorillonites. Kaolinite and illite particles are also found primarily at the aqueous/aqueous interface, while the montmorillonite particles (more visible in the transmitted light images) are found mainly in the PEG-rich phase (Figs 2 and 3).

Figure 2
Figure 2

Confocal optical microscope images of clay particles with 1:1 volume ratio from 15%/15% w/w stock PEG-Dx ATPS. Fluorescent-labeled Dx (red) and PEG (green) have been used to image Dx-rich phase droplets and continuous PEG-rich phase. Clay particles appear red in fluorescence images due to adsorption of fluorescently labeled Dx to particle surface. Right images show overlay of fluorescence channels and left images show transmitted light for samples containing: (A) Kaolinite, (B) Na-rich montmorillonite, (C) Ca-rich montmorillonite and (D) illite in PEG-Dx ATPS.

Figure 3
Figure 3

Different volume ratio of ATPS, 20:1 PEG-rich phase: Dx-rich phase from 15%/15% w/w PEG-Dx stock ATPS. Confocal Microscope images of clay particles with fluorescent-labeled Dx (red) and PEG (green) added to aid visualization of Dx-rich phase droplets and continuous PEG-rich phase. Right images show overlay of fluorescence channels and left images show transmitted light for samples containing: (A) Kaolinite, (B) Na-rich montmorillonite, (C) Ca-rich montmorillonite and (D) illite in PEG-Dx ATPS.

Literature reports indicate that adsorption of PEG57, 58 and Dx59 polymers onto clays or other silica and alumina surfaces is likely. In Figs 2 and 3 we observe association of the Alexa647-labeled dextran, but not the Alexa488-labeled PEG, to the clay particles. Polymer adsorption could impact particle wetting by the two aqueous phases and hence any differences in polymer adsorption between the clay types may explain the observed differences in particle distribution in the ATPS. To better understand the observed staining of clays with Alexa647-Dx, we performed a series of control experiments in which the labeled polymers or labels alone (not attached to a polymer) were incubated with each of the clay samples in water (i.e., in the absence of unlabeled polymers). These data are shown and discussed further in Supporting Information (see Supporting Figs S6S9). We concluded that kaolinite and illite particles are interacting preferentially with labeled Dx, which makes them appear red in fluorescence micrographs, while the montmorillonites do not interact themselves preferentially with either PEG or Dx polymers but a minority population of impurity particles interacts with labeled dextran in the montmorillonite samples. In Fig. 2C, fluorescently-labeled impurity minerals in the Ca-rich montmorillonite sample are found at the aqueous/aqueous interface, but do not provide stabilization against droplet coalescence (note large size and polydispersity of droplets). At the 20:1 volume ratio, these impurity particles are less prominent at the interfaces (Fig. 3C).

The most notable difference between the volume ratios was that larger Dx-rich droplets were observed when more Dx-rich phase was present (compare Figs 2 and 3). Additionally, more labeled Dx is visible in the Dx-rich droplets for the montmorillonite samples at 20:1 as compared to 1:1 volume ratio; this is because the same amount of labeled Dx was present in both samples, and it is more concentrated for smaller Dx-rich phase volume. This is not observed for kaolinite or illite samples due to the strong adsorption of labeled Dx to the particles in those samples. Dx-rich droplets containing kaolinite have irregular shapes indicating arrested coalescence unlike the other samples we have investigated60.

Although samples for a given clay type were similar regardless of volume ratio, differences between the four clays are apparent. Kaolinite and illite, which interact preferentially with the Dx polymer, showed greater interfacial accumulation than either montmorillonite and formed essentially complete coatings around the Dx-rich phase droplets (Table 2). Some interfacially-adsorbed clay particles could also be seen in montmorillonite samples, particularly for the Ca-rich montmorillonite sample, although the majority of montmorillonite particles were found in the PEG-rich phase. The interfacial particles here appear to preferentially be non-montmorillonite impurity particles, as evidenced by their strong labeling with fluorescent dextran (see Supporting Fig. 6 and Supporting Discussion). These observations on clay distribution in the ATPS are generally consistent with the differences in polymer adsorption and bulk partitioning in Table 2 and Supplementary Figs S6S9. Additionally, kaolinite samples had non-spherical clay-coated droplets that contained some interior clay particles and in some cases also what appear to be inclusions of PEG-rich phase within the Dx-rich droplets (see Fig. 3A). Dx-rich droplets in the other samples were spherical, with uniform interiors. As the interfacial area gets reduced during coalescence, surface coverage of droplets increase leading to jamming at the interface without further shape relaxation leading to non-uniform shapes. The non-spherical droplets indicate the presence of arrested coalescence of kaolinite-coated droplets60, 61.

Table 2: Summary of clay mineral behavior in 15%/15% w/w PEG/Dx ATPS.

Over time, illite or kaolinite clay-clad particles sedimented to the bottom of the sample chamber but they did not coalesce even when droplets were in contact. In contrast, droplets in montmorillonite-containing samples coalesced readily upon contact, with stabilization only occurring when accumulations of clay particles in the PEG-rich phase physically prevented Dx-rich droplets from contacting each other (Supplementary Fig. S10). The fact that interfacial coatings of illite or kaolinite can stabilize Dx-rich droplets against coalescence in a continuous PEG-rich phase is perhaps counterintuitive since these clays appear to be wet preferentially by the Dx-rich phase in bulk partitioning experiments, and also are coated with a layer of adsorbed polymer (Table 2). When spherical colloidal particles provide steric stabilization, they are generally preferentially wetted by the continuous phase (Bancroft rule)39, 62,63,64. Indeed, clay particles form oil-in-water Pickering and water-in-oil inverse Pickering emulsions depending on their surface hydrophilicity/hydrophobicity31, 34, 36. Our observations are more similar to those of Erne and coworkers for gibbsite nanoplates in a Dx/gelatin ATPS, which stabilized droplets of either phase in the other40. Three-phase contact angle estimates from measurements in which Dx-rich droplets surrounded by PEG-rich phase were placed on clay-coated substrates indicated contact angles greater than 90° for all four clay types (Fig. 4 and Supplementary Fig. S11). Kaolinite and illite, which interact with Dx and form clay-clad droplets, had contact angles, θ ~ 101 ± 7° and 107 ± 5°, respectively, while estimated contact angles for Na-rich and Ca-rich montmorillonite, which do not show effective droplet stabilization, were 128 ± 9° and 135 ± 10°, respectively (Fig. 4B). We interpret the relative lack of wetting by the Dx-rich phase as a consequence of the similarity between the two aqueous phases and the roughness of the clay-coated surfaces, and in the case of the montmorillonite samples also to the lack of chemical interaction with the Dx polymer.

Figure 4
Figure 4

(A) Representative photograph of Dx-rich phase droplets sitting on illite-covered glass slides surrounded by a PEG-rich continuous phase, collected to estimate contact angles for clay microparticles in the ATPS, and (B) calculated three-phase contact angles from multiple images for different Dx-rich droplets on surfaces that were coated with clay were listed (Error is standard deviation of contact angle measurements).

Effect of increasing interfacial tension

We compared clay-containing ATPS prepared using stock solutions containing 15 wt% of each polymer and 20% of each polymer. As expected, the higher polymer concentration led to higher interfacial tension, γ (Table 3). Using spinning drop tensiometer, we found γ = 0.357 ± 0.008 mN/m and 0.746 ± 0.014 mN/m for 15%/15% and 20%/20% w/w PEG 8 kDa-Dx 10 kDa, respectively (see Materials and Methods). We increased the polymer percentage gradually and checked the interfacial results for polymer concentration between 15%/15% and 20%/20% w/w PEG 8 kDa-Dx 10 kDa (Supplementary Fig. S12). Increasing the interfacial tension by a factor of more than two-fold might be expected to increase adsorption of clay microparticles at the ATPS interface. Qualitatively, our results were very similar for the two different polymer percentage ATPS, however (compare Fig. 5, with higher γ, to Fig. 3). Notably, the montmorillonite particles still fail to accumulate appreciably at the interface even at the higher γ. There appears to be more internal structure in the Dx-rich droplets, particularly for Ca-rich montmorillonite, at the higher polymer concentrations. This could be a result of greater solution viscosity in the more concentrated ATPS.

Table 3: Physical properties of 15%/15% and 20%/20% w/w PEG/Dx ATPS.
Figure 5
Figure 5

Clay distribution in ATPS with higher polymer concentration. Optical microscope images showing clay particles with 20:1 volume ratio of a stock 20%/20% w/w PEG/Dx ATPS. Left-hand images show transmitted light, and right-hand images show overlay of red and green confocal fluorescence channels for samples containing: (A) Kaolinite, (B) Na-rich montmorillonite, (C) Ca-rich montmorillonite and (D) illite. Fluorescent-labeled Dx (red) and PEG (green) have been included to aid visualization of the Dx-rich phase droplets and PEG-rich continuous phase.

Inverted emulsions

Reversing the volume ratio from 20:1 to 1:20 PEG-rich phase:Dx-rich phase led to formation of clay-stabilized PEG-rich droplets surrounded by Dx-rich continuous phase (Fig. 6). Samples containing kaolinite showed relatively spherical, uniform clay-stabilized droplets that resisted coalescence. Na-rich montmorillonite and Ca-rich Montmorillonite did not form stable droplets for the 1: 20 PEG-rich phase: Dx-rich phase ratio (droplets seen in Fig. 6B,C were not stable against coalescence). Samples containing illite formed clay-coated PEG-rich droplets that were more heterogeneous in their coatings and less stable against droplet coalescence than for the 20:1 PEG-rich phase: Dx-rich phase ratio (Fig. 6D). We observed similar trends for both of the ATPS compositions (15%/15% and 20%/20% w/w 10 PEG-Dx ATPS, see Supplementary Fig. S13 for 15%/15%).

Figure 6
Figure 6

Clay distribution in ATPS having reverse volume ratio. For 20%/20% w/w PEG 8 kDa-Dx 10 kDa using volume ratio of 1:20 PEG-rich phase: Dx-rich phase with (A) Kaolinite (KGa-2), (B) Na-rich montmorillonite (SWy-2), (C) Ca-rich montmorillonite (STx-1b) and (D) NX-illite. Labeled Dx (red, 2 μM final concentration) and labeled PEG (green, 2 μM final concentration) have been used for fluorescence imaging. Left-hand images show transmitted light, and right-hand images show overlay of red and green confocal fluorescence channels. Continuous phase is Dx-rich phase while droplets are PEG-rich phase.

Darkfield imaging to directly visualize clay particles

Darkfield microscopy was also used to more clearly image clay microparticles at the aqueous-aqueous interface without need of fluorescent labels. Samples without clay have poor contrast at the ATPS phase boundary (Fig. 7A,B), but when clay is present it is apparent at this interface and provides stabilization against droplet coalescence. Figure 7C,D shows PEG-in Dx droplets stabilized by kaolinite and Dx-in-PEG droplets stabilized by illite, respectively. Darkfield imaging for these clay-clad droplet samples is consistent with the fluorescence data shown above, indicating that the fluorescent labels are not playing an important role in particle adsorption at the interface.

Figure 7
Figure 7

Darkfield optical microscope images showing ATPS before (A,B) and after (C,D) addition of clay microparticles. Kaolinite-stabilized PEG-rich droplets in Dx-rich continuous phase (C) (phase volume ratio 1:20 PEG-rich: Dx-rich), illite-stabilized Dx-rich droplets in PEG-rich continuous phase (D) (phase volume ratio 20:1 PEG-rich: Dx-rich) are formed. All scale bars represent 20 µm. Stock ATPS for both samples was 15%/15% w/w PEG 8 kDa-Dx 10 kDa.

Clay particles as catalysts for a simple reaction

We next evaluated the catalytic performance of the clay microparticle-containing ATPS. Concentration of reactants by surface adsorption has been suggested as one mechanism for surface-catalyzed polymerization65. In an encouraging recent report, Mann and coworkers explored the catalytic activity of titania nanosheets sequestered into coacervates used as micro-droplet reactors for photocatalytic degradation66. Differences in sequestration of organic dyes into the droplets provided reaction selectivity in that system. There have been no studies as yet of natural clays and their catalytic activity in neutral polymer ATPS like the PEG/Dx system used here. Since Dx was observed adsorbing to the surfaces of the clay particles, competition for adsorption sites could be expected to reduce the effectiveness of clay mineral surfaces as catalysts in ATPS. We nonetheless experimentally tested the feasibility of implementing these systems as catalytically-enabled aqueous phase droplet microreactors. As proof-of-principle, we chose the reaction of o-phenylenediamine (OPD) with hydrogen peroxide to form 2, 3 diaminophenazine. This reaction, commonly catalyzed by the enzyme horseradish peroxidase, can be followed spectrophotometrically by product absorbance at 417 nm. Although many colorimetric reagents exist for assaying peroxidase activity, we chose OPD due to its relative hydrophilicity as compared with substrates such as Amplex red or 3,3′,5,5′-tetramethylbenzidine (TMB). Aumiller et al. recently reported significant effects of macromolecular crowding agents including PEG and Dx67. Substrate hydrophobicity was linked to greater interactions with PEG present in the solution as a macromolecular crowder, and these interactions greatly reduced enzymatic activity due to sequestration of the substrate. These effects were found to be stronger for TMB than OPD in that work.

In our experiments clay microparticles were used as catalysts for OPD reaction with peroxide in the PEG/Dx ATPS. Reactions were performed in quiescent solutions of 20:1 ratio of Dx-rich phase/PEG-rich phase and followed over time for approximately one day; at each time point samples were centrifuged to sediment clay microparticles before spectrophotometric product determination in the supernatant (Supplementary Figs S1418). Controls were also performed in buffer and single phases, and in the absence of clays or OPD (Supplementary Figs S14S16). Quantification of product absorbance at 417 nm indicated that all four clays (kaolinite, both montmorillonites, and illite) had slightly higher activity in the ATPS than in buffer alone (Fig. 8 and Supplementary Figs S17S18). Illite was most active for this reaction in our experiments, both in buffer and in the ATPS. Na-rich montmorillonite samples also showed good catalytic activity but the product remained associated with the particles and was not distributed in the solution (Supplementary Fig. S19; we note that it was not possible to distinguish between activity and adsorption to montmorillonite vs. its impurity minerals in these experiments). When clay was not present, product was not observed.

Figure 8
Figure 8

OPD reaction progress. Reaction product absorbance at 417 nm in buffer with substrates without presence of illite (blue), in buffer with illite and substrates (black) and in 20:1 ratio of Dx-rich phase/PEG-rich phase with substrates (red). Hydrogen peroxide was held in excess at 8.8 mM and OPD was 500 µM in 100 mM HEPES buffer, pH 7.5. Error bars represent the standard deviation of the measurements.

The ability of illite-clad ATPS droplets to catalyze this reaction is an encouraging proof of concept for natural clay microparticles providing catalytic capabilities to droplets formed by aqueous-aqueous phase coexistence. Despite adsorption of Dx to the illite surface (see Table 2), reaction rates were slightly higher for illite in the ATPS than in buffer alone. This may be due to the partial Pickering emulsification of the illite/ATPS system, where clay-clad droplets remain suspended for many hours, facilitating reaction of the illite with OPD in solution. We note that the reaction product 2, 3 diaminophenazine did not accumulate in either phase of the ATPS (its partitioning coefficient, K, was 1.01 ± 0.01, where K = CP/CD and CP and CD represent the concentrations of the product in the PEG-rich and Dx-rich phases, respectively). Based on its similar structure and smaller size, the OPD substrate is also not expected to accumulate in either phase. Further rate enhancements should be achievable by taking advantage of substrates and/or products that exhibit strong partitioning between the two aqueous phases to facilitate access to the catalytic clay particles.


The work presented here shows the rich behavior of natural clays in the PEG/Dx ATPS, with surprisingly different observations for kaolinite, montmorillonite and illite particles despite their similar chemical compositions and surface charge. Although bulk Pickering emulsions were not stable over long times due to sedimentation of clay-coated droplets, natural clay microparticles of all types tested adsorbed at the aqueous/aqueous interface to at least some degree. We observed several basic types of geometries that combined clay microparticles with the droplet phase of the ATPS. Kaolinite and illite particles adsorbed readily at the interface to form clay-clad droplets for ATPS with either Dx-rich or PEG-rich dispersed phases. Montmorillonites showed the least accumulation at the interface; montmorillonite-containing Dx-rich droplets were common despite the majority of montmorillonite particles remaining in the PEG-rich phase. Stabilization of Dx-rich droplets against coalescence was possible when relatively large montmorillonite particles accumulated between the droplets; this stabilization mechanism was most effective at high local particle concentrations. We evaluated the ability of ATPS that contained natural clay microparticles to catalyze a simple reaction and found that illite in particular not only retained its catalytic capability despite Dx adsorption to the particles in the ATPS, but in fact the rate was slightly enhanced for the illite-stabilized droplet samples as compared to illite in buffer alone. This is to the best of our knowledge the first paper to describe distributions of natural clay microparticles in ATPS and demonstrate their retention of activity in clay-stabilized ATPS droplets. As such, our findings support the potential of combining catalytic natural mineral particles with aqueous microcompartments to form primitive microreactors, which could be relevant to abiotic chemistry on the early Earth. Although the specific ATPS composition used here may not be directly relevant to early Earth scenarios, a variety of prebiotic polymers were present15, 68, and could have participated in aqueous/aqueous phase separation to generate systems similar to those studied here.

Materials and Methods

Chemicals and Materials

Three types of clay were supplied from the Clay Mineral Society Source Clays Repository: kaolinite, Warren County, Georgia, USA (KGa-2); Na-rich montmorillonite, Crook County, Wyoming, USA (SWy-2); and Ca-rich montmorillonite, Gonzales County, Texas, USA (STx-1b). NX-illite was obtained from Arginotec, NX Nanopowder, B + M Notenkämper, Munich, Germany. NX-Illite is composed of illite, illite-smectite mixed layer, feldspar, kaolinite, quartz and carbonate52.

PEG 8 kDa, dextran 10 kDa, 4-(2-hydroxyethyl)-1-piperazineethanesulfonic acid (HEPES), HEPES sodium salt, sodium bicarbonate, o-phenylenediamine tablets, hydrogen peroxide and 2,3-diaminophenazine were purchased from Sigma-Aldrich (St. Louis, MO). Labeled polymer mPEG-NH2 MW 5000 was purchased from Shearwater Polymers. Alexa Fluor 647-Dextran 10 kDa, Alexa Fluor 488 labeling kits and 20 mm diameter by 0.5 mm deep press-to-seal silicone isolators were obtained from Life Technologies (Carlsbad, CA). Water was deionized to a resistance of 18.2 MΩ with Barnstead NANOpure Diamond water purification system (Van Nuys, CA) and used for all experiments.

Preparation of ATPS

Two different stock ATPS were prepared at 10 g total mass: (1) 15%/15% w/w by dissolving 1.50 g PEG 8 kDa, 1.50 g dextran (Dx)10 kDa in 7.00 g 100 mM pH 7.5 HEPES buffer for; and (2) 20%/20% w/w by dissolving 2.00 g PEG 8 kDa, 2.00 g Dx 10 kDa in 6.00 g 100 mM pH 7.5 HEPES buffer. These mixtures were stirred in a glass container at 37 °C for several hours until the polymers were completely dissolved, then either left overnight or centrifuged at 3000 × g for phase separation. Different volume ratios of PEG-rich to Dx-rich phases used in the experiments were obtained from phase separated stock solutions and remixed in desired ratios as previously described24.

Phase composition determination

Polymer concentration of PEG-rich phase and Dx-rich phase were determined using refractometry and polarimetry29. Abbe Autorefractometer (Leica Geosystems, Norcross, GA) was used to measure refractive index of each phases. Polarimetry measurements were carried out with model No. 343 Polarimeter (PerkinElmer, Billerica, MA). First, concentration of optically active Dx 10 kDa was determined by polarimetry by generating standard curve. Later concentration of PEG was determined by refractometry. Standard curves for PEG and Dx were prepared with known concentrations. Each sample was measured in triplicate using polarimetry and refractometry. Dx contribution to total refractive index was subtracted and remaining refractive index was used to calculate the concentration of PEG in each phases.

PEG Labeling

mPEG-NH2 MW 5000 was labeled with Alexa Fluor-488 in the presence of 0.1 M sodium bicarbonate. The reaction was covered by aluminum foil and stirred at room temperature for 3 h. Free dye was removed using an Amicon 300 MWCO filter with centrifugation at 14000 g.

Dynamic Light Scattering and Zeta Measurements

Suspended stock solution of clay 10 µL was diluted by adding 1 mL DI water for dynamic light scattering measurements except Na-rich montmorillonite, 15 µL of suspended stock was diluted for it. From suspended stock solution of clay 10 µL was diluted by adding 1 mL of 100 mM pH 7.5 HEPES buffer, except Na-rich montmorillonite, 15 µL of stock was diluted with 100 mM pH 7.5 HEPES buffer, for Zeta Potential measurements. Measurements were done in triplicate using a Malvern Zetasizer NanoZS.

Scanning electron microscopy (SEM)

Clays were imaged by FEI NanoSEM 630 FESEM at 1 keV and 700 eV. In order to prevent charging during imaging the clay particles, which are nonconductive, we followed the method of Veghte et al.51. Clay particles were impacted by a cascade impactor (PIXE International Corp., Tallahassee FL) over the silicon wafer chips (Virginia Semiconductor Inc., Fredericksburg VA). Then, sparse particles over the silicon wafer were imaged.

Confocal Fluorescence Microscopy

Images were collected with a Leica TCS SP5 inverted confocal microscope at 63x magnification to image the behavior of clay particles in ATPS. Alexa 488-labeled PEG 5k and Alexa Fluor 647-Dx 10 kDa were excited with a 488 nm argon ion laser and 633 nm, respectively. Samples were prepared by using 20:1 PEG-rich phase: Dx-rich phase and 1:20 PEG-rich ratios. Samples were vortexed before imaging. Glass coverslips used in microscopy were silanized in gas phase with dichloromethylsilane and used with press-to-seal spacer69.

Darkfield Microscopy

Images were obtained with Nikon TE200 inverted microscope using 100x oil objective with iris NA 0.5–1.3 and darkfield oil condenser NA 1.2–1.43 with illumination from a halogen lamp.

Determination of ATPS interfacial tension by Spinning Drop Tensiometry

Different percentages of ATPS were prepared and phase separated by centrifugation at 5000 × g for 10 minutes. Krüss SITE 100 spinning drop tensiometer was used. Heavy phase, Dx-rich phase, was loaded to capillary tube and then light phase (4 µL) was injected. Triplicate tensiometry measurements were taken at 9, 10, 11 and 12k rpm and were in agreement.

Contact Angle/Pendant Drop

Due to the small size and to the heterogeneity in both particle size and particle shape for each clay sample, it was not possible to determine their contact angles with the liquid phases while they are adsorbed at the liquid/liquid interface. Therefore we followed the method of Vis et al.40. Clay particles were deposited on glass slides by vertical deposition method70. Three-phase macroscopic contact angle between Dx-rich droplets in PEG-rich phase were imaged at least three times per sample, then the contact angle was measured from both left and right sides of the droplets with ImageJ71. Each measurement repeated at least three times.

Glass slides (24 mm × 30 mm) were cut in half using a diamond pen in order to fit them into vials. Then they were immersed in 1:1 hydrochloric acid and methanol mixture for an hour. Glass slides were rinsed well and dried with nitrogen. Each slide was placed in a vial with an angle about 30° and dilute solution of clay solution used to fill the vials. They were left on a heating plate at 100 °C overnight to form a layer of clay on the glass slides. Only surfaces well-covered with clay over their entire surface were used. PEG/Dx ATPS (15%/15% w/w) solutions were prepared and allowed to equilibrate as described and then the phases were separated. PEG-rich phase was used to fill the rectangular container and 250 µL pipette tip was filled with denser Dx-rich phase. The tip was immersed in PEG-rich phase containing clay covered glass slide. 3 µL droplets were then dispensed over the clay-covered surface for several times with different glass slides and droplets. Images were taken using a Pendat drop instrument (Ramè-hart Model 295) and three-phase contact angle were calculated from both left and right sides of droplets.

Clay Catalyzed Reaction

Reaction progress was followed using an Agilent 8453 diode array UV-visible spectrometer with Agilent ChemStation software. All measurements were repeated for three times and monitored at 417 nm. Hydrogen peroxide was held in excess at 8.8 mM and OPD was 500 µM in 100 mM HEPES buffer, pH 7.5. OPD tablet was dissolved in HEPEs buffer and used immediately. 10% clay stock was prepared and diluted to 1% in the reaction mixture instead of catalyst. Reaction product (2,3-diaminophenazine) was monitored by UV-Vis at 417 nm (see Fig. 9). As the reaction progressed, the solution changed color to orange–brown67.

Figure 9
Figure 9

OPD reaction scheme.

Partitioning of Reaction Product

Partitioning of reaction product was determined by measuring the absorbance in each phase. The reaction product, 2,3-diaminophenazine, was dissolved in 1 mL ATPS at a 1:1 volume ratio of PEG-rich:Dx-rich phase with final concentration of at 500 µM. ATPS stock solution was prepared with composition 15%/15% w/w PEG 8 kDa/Dx 10 kDa. After mixing, phases were separated by centrifugation. The concentration of product in each phase was calculated by measuring absorbance of three samples for each phase using an Agilent 8453 diode array UV-visible spectrometer with Agilent ChemStation software. Partitioning coefficients are reported as K = Cp/CD, where CP and CD represent the concentration of product in PEG-rich phase and Dx-rich phase, respectively. Absorbance values were corrected for each phase.

Additional Information

Publisher's note: Springer Nature remains neutral with regard to jurisdictional claims in published maps and institutional affiliations.


  1. 1.

    Moore, D. M. & Reynolds, R. C. X-ray diffraction and the identification and analysis of clay minerals. 2nd edn, (Oxford University Press, 1997).

  2. 2.

    Burst, J. F. The application of clay minerals in ceramics. Applied Clay Science 5, 421–443, doi:10.1016/0169-1317(91)90016-3 (1991).

  3. 3.

    Rong, D., Kim, Y. II & Mallouk, T. E. Electrochemistry and photoelectrochemistry of pillared-clay-modified electrodes. Inorganic Chemistry 29, 1531–1535, doi:10.1021/ic00333a018 (1990).

  4. 4.

    Zeng, Q. H., Yu, A. B., Lu, G. Q. & Paul, D. R. Clay-based polymer nanocomposites: research and commercial development. J Nanosci Nanotechnol 5, 1574–1592, doi:10.1166/jnn.2005.411 (2005).

  5. 5.

    Nagendrappa, G. Organic synthesis using clay and clay-supported catalysts. Applied Clay Science 53, 106–138, doi:10.1016/j.clay.2010.09.016 (2011).

  6. 6.

    Zhou, C. H. Clay mineral-based catalysts and catalysis. Applied Clay Science 53, 85–86, doi:10.1016/j.clay.2011.04.015 (2011).

  7. 7.

    Pinnavaia, T. J. Intercalated Clay Catalysts. Science 220, 365–371, doi:10.1126/science.220.4595.365 (1983).

  8. 8.

    Bernal, J. D. The Physical Basis of Life. P Phys Soc Lond A 62, 537–558, doi:10.1088/0370-1298/62/9/301 (1949).

  9. 9.

    Ferris, J. P. & Ertem, G. Oligomerization of ribonucleotides on montmorillonite: reaction of the 5′-phosphorimidazolide of adenosine. Science 257, 1387–1389, doi:10.1126/science.1529338 (1992).

  10. 10.

    Hanczyc, M. M., Mansy, S. S. & Szostak, J. W. Mineral surface directed membrane assembly. Origins of life and evolution of the biosphere: the journal of the International Society for the Study of the Origin of Life 37, 67–82, doi:10.1007/s11084-006-9018-5 (2007).

  11. 11.

    Cleaves, H. J. 2nd et al. Mineral-organic interfacial processes: potential roles in the origins of life. Chemical Society reviews 41, 5502–5525, doi:10.1039/c2cs35112a (2012).

  12. 12.

    Hanczyc, M. M., Fujikawa, S. M. & Szostak, J. W. Experimental models of primitive cellular compartments: Encapsulation, growth, and division. Science 302, 618–622, doi:10.1126/science.1089904 (2003).

  13. 13.

    Hazen, R. M. & Sverjensky, D. A. Mineral surfaces, geochemical complexities, and the origins of life. Cold Spring Harbor perspectives in biology 2, a002162, doi:10.1101/cshperspect.a002162 (2010).

  14. 14.

    Hashizume, H. Role of Clay Minerals in Chemical Evolution and the Origins of Life. doi:10.5772/50172 (2012).

  15. 15.

    Keating, C. D. Aqueous Phase Separation as a Possible Route to Compartmentalization of Biological Molecules. Accounts Chem Res 45, 2114–2124, doi:10.1021/Ar200294y (2012).

  16. 16.

    Mann, S. Systems of Creation: The Emergence of Life from Nonliving Matter. Accounts Chem Res 45, 2131–2141, doi:10.1021/ar200281t (2012).

  17. 17.

    Koonin, E. V. An RNA-making reactor for the origin of life. P Natl Acad Sci USA 104, 9105–9106, doi:10.1073/pnas.0702699104 (2007).

  18. 18.

    Dewey, D. C., Strulson, C. A., Cacace, D. N., Bevilacqua, P. C. & Keating, C. D. Bioreactor droplets from liposome-stabilized all-aqueous emulsions. Nature communications 5, 4670, doi:10.1038/ncomms5670 (2014).

  19. 19.

    Stano, P., Carrara, P., Kuruma, Y., de Souza, T. P. & Luisi, P. L. Compartmentalized reactions as a case of soft-matter biotechnology: synthesis of proteins and nucleic acids inside lipid vesicles. J Mater Chem 21, 18887–18902, doi:10.1039/C1JM12298C (2011).

  20. 20.

    Chen, I. A. & Walde, P. From Self-Assembled Vesicles to Protocells. Cold Spring Harbor perspectives in biology 2 (2010).

  21. 21.

    Oparin, A. I. The origin of life on the earth. (Academic Press, 1957).

  22. 22.

    Rasmussen, S. Protocells: Bridging Nonliving and Living Matter. (MIT Press, 2009).

  23. 23.

    Frankel, E. A. D. D. C., Keating, C. D. In Astrobiology: An Evolutionary Approach (ed. V. M. Kolb) (CRC Press, Taylor & Francis Group, 2015).

  24. 24.

    Strulson, C. A., Molden, R. C., Keating, C. D. & Bevilacqua, P. C. RNA catalysis through compartmentalization. Nat Chem 4, 941–946, doi:10.1038/Nchem.1466 (2012).

  25. 25.

    Walter, H. Partitioning In Aqueous Two–Phase System: Theory, Methods, Uses, And Applications To Biotechnology. (Elsevier, 2012).

  26. 26.

    Hatti-Kaul, R. Aqueous two-phase systems: methods and protocols. Vol. 11 (Springer Science & Business Media, 2000).

  27. 27.

    Tolstoguzov, V. Some thermodynamic considerations in food formulation. Food Hydrocolloid 17, 1–23, doi:10.1016/S0268 (2003).

  28. 28.

    Zaslavsky, B. Y. Aqueous two-phase partitioning: physical chemistry and bioanalytical applications. (CRC Press, 1994).

  29. 29.

    Davis, B. W. et al. Colocalization and Sequential Enzyme Activity in Aqueous Biphasic Systems: Experiments and Modeling. Biophys J 109, 2182–2194, doi:10.1021/jp501126v (2015).

  30. 30.

    Tang, T. Y. D. et al. Fatty acid membrane assembly on coacervate microdroplets as a step towards a hybrid protocell model. Nat Chem 6, 527–533, doi:10.1038/nchem.1921 (2014).

  31. 31.

    Binks, B. P., Clint, J. H. & Whitby, C. P. Rheological behavior of water-in-oil emulsions stabilized by hydrophobic bentonite particles. Langmuir 21, 5307–5316, doi:10.1021/La050255w (2005).

  32. 32.

    Lagaly, G., Reese, M. & Abend, S. Smectites as colloidal stabilizers of emulsions - I. Preparation and properties of emulsions with smectites and nonionic surfactants. Applied Clay Science 14, 83–103, doi:10.1016/S0169-1317(98)00051-9 (1999).

  33. 33.

    Yan, N. X. & Masliyah, J. H. Adsorption and Desorption of Clay Particles at the Oil-Water Interface. Journal of Colloid and Interface Science 168, 386–392, doi:10.1006/jcis.1994.1434 (1994).

  34. 34.

    Ashby, N. P. & Binks, B. P. Pickering emulsions stabilised by Laponite clay particles. Physical Chemistry Chemical Physics 2, 5640–5646, doi:10.1039/B007098J (2000).

  35. 35.

    Abend, S., Bonnke, N., Gutschner, U. & Lagaly, G. Stabilization of emulsions by heterocoagulation of clay minerals and layered double hydroxides. Colloid Polym Sci 276, 730–737, doi:10.1007/s003960050303 (1998).

  36. 36.

    Voorn, D. J., Ming, W. & van Herk, A. M. Polymer-clay nanocomposite latex particles by inverse pickering emulsion polymerization stabilized with hydrophobic montmorillonite platelets. Macromolecules 39, 2137–2143, doi:10.1021/Ma052539t (2006).

  37. 37.

    Li, W. et al. Oil-in-water emulsions stabilized by Laponite particles modified with short-chain aliphatic amines. Colloids and Surfaces A: Physicochemical and Engineering Aspects 400, 44–51, doi:10.1016/j.colsurfa.2012.02.044 (2012).

  38. 38.

    Binks, B. P. & Horozov, T. S. Colloidal Particles at Liquid Interfaces. (Cambridge University Press, 2006).

  39. 39.

    Aveyard, R., Binks, B. P. & Clint, J. H. Emulsions stabilised solely by colloidal particles. Adv Colloid Interfac 100, 503–546 (2003).

  40. 40.

    Vis, M. et al. Water-in-Water Emulsions Stabilized by Nanoplates. ACS Macro Letters, 965–968, doi:10.1021/acsmacrolett.5b00480 (2015).

  41. 41.

    Yan, N. X., Gray, M. R. & Masliyah, J. H. On water-in-oil emulsions stabilized by fine solids. Colloid Surface A 193, 97–107, doi:10.1016/S0927-7757(01)00748-8 (2001).

  42. 42.

    Balakrishnan, G., Nicolai, T., Benyahia, L. & Durand, D. Particles Trapped at the Droplet Interface in Water-in-Water Emulsions. Langmuir 28, 5921–5926, doi:10.1021/la204825f (2012).

  43. 43.

    Firoozmand, H., Murray, B. S. & Dickinson, E. Interfacial Structuring in a Phase-Separating Mixed Biopolymer Solution Containing Colloidal Particles. Langmuir 25, 1300–1305, doi:10.1021/la8037389 (2009).

  44. 44.

    Nguyen, B. T., Nicolai, T. & Benyahia, L. Stabilization of Water-in-Water Emulsions by Addition of Protein Particles. Langmuir 29, 10658–10664, doi:10.1021/la402131e (2013).

  45. 45.

    Buzza, D. M. A., Fletcher, P. D. I., Georgiou, T. K. & Ghasdian, N. Water-in-Water Emulsions Based on Incompatible Polymers and Stabilized by Triblock Copolymers-Templated Polymersomes. Langmuir 29, 14804–14814, doi:10.1021/la403356j (2013).

  46. 46.

    Albertsson, P.-Å. Partition of Cell Particles and Macromolecules. (Wiley, 1986).

  47. 47.

    Miller, M. A. & Bailey, L. P. (Miller Accounting Publications, New York, 1982).

  48. 48.

    Brown, G. Crystal-Structures of Clay-Minerals and Related Phyllosilicates. Philos T R Soc A 311, 221–240, doi:10.1098/rsta.1984.0025 (1984).

  49. 49.

    Grim, R. E. Clay mineralogy. 2d edn, (McGraw-Hill, 1968).

  50. 50.

    Martin, R. T. et al. Report of the Clay-Minerals-Society Nomenclature Committee - Revised Classification of Clay Materials. Clay Clay Miner 39, 333–335, doi:10.1346/Ccmn.1991.0390315 (1991).

  51. 51.

    Veghte, D. P. & Freedman, M. A. Facile Method for Determining the Aspect Ratios of Mineral Dust Aerosol by Electron Microscopy. Aerosol Science and Technology 48, 715–724, doi:10.1080/02786826.2014.920484 (2014).

  52. 52.

    Broadley, S. L. et al. Immersion mode heterogeneous ice nucleation by an illite rich powder representative of atmospheric mineral dust. Atmos Chem Phys 12, 287–307, doi:10.5194/acp-12-287-2012 (2012).

  53. 53.

    Chorom, M. & Rengasamy, P. Dispersion and zeta potential of pure clays as related to net particle charge under varying pH, electrolyte concentration and cation type. Eur J Soil Sci 46, 657–665, doi:10.1111/j.1365-2389.1995.tb01362.x (1995).

  54. 54.

    Mackinnon, I. D. R., Uwins, P. J. R., Yago, A. & Page, D. Kaolinite Particle Sizes in the Less-Than-2-Mu-M Range Using Laser Scattering. Clays and Clay Minerals 41, 613–623, doi:10.1346/Ccmn.1993.0410512 (1993).

  55. 55.

    Nadeau, P. H. The Physical Dimensions of Fundamental Clay Particles. Clay Miner 20, 499–514, doi:10.1180/claymin.1985.020.4.06 (1985).

  56. 56.

    Cacace, D. N., Rowland, A. T., Stapleton, J. J., Dewey, D. C. & Keating, C. D. Aqueous Emulsion Droplets Stabilized by Lipid Vesicles as Microcompartments for Biomimetic Mineralization. Langmuir 31, 11329–11338, doi:10.1021/acs.langmuir.5b02754 (2015).

  57. 57.

    Zhao, X., Urano, K. & Ogasawara, S. Adsorption of Polyethylene-Glycol from Aqueous-Solution on Montmorillonite Clays. Colloid Polym Sci 267, 899–906, doi:10.1007/BF01410338 (1989).

  58. 58.

    Hu, X. B. et al. Preferential Adsorption of Poly(ethylene glycol) on Hectorite Clay and Effects on Poly(N-isopropylacrylamide)/Hectorite Nanocomposite Hydrogels. Langmuir 26, 4233–4238, doi:10.1021/la903298n (2010).

  59. 59.

    Kwon, K. D., Green, H., Bjoorn, P. & Kubicki, J. D. Model bacterial extracellular polysaccharide adsorption onto silica and alumina: Quartz crystal microbalance with dissipation monitoring of dextran adsorption. Environ Sci Technol 40, 7739–7744, doi:10.1021/Es061715q (2006).

  60. 60.

    Pawar, A. B., Caggioni, M., Ergun, R., Hartel, R. W. & Spicer, P. T. Arrested coalescence in Pickering emulsions. Soft Matter 7, 7710–7716, doi:10.1039/C1SM05457K (2011).

  61. 61.

    Manoharan, V. N. Colloidal spheres confined by liquid droplets: Geometry, physics, and physical chemistry. Solid State Commun 139, 557–561, doi:10.1016/j.ssc.2006.04.038 (2006).

  62. 62.

    Binks, B. P. Relationship between Microemulsion Phase-Behavior and Macroemulsion Type in Systems Containing Nonionic Surfactant. Langmuir 9, 25–28, doi:10.1021/la00025a008 (1993).

  63. 63.

    Finkle, P., Draper, H. D. & Hildebrand, J. H. The theory of emulsification. J Am Chem Soc 45, 2780–2788 (1923).

  64. 64.

    Pickering, S. U. Emulsions. J Chem Soc 91, 2001–2021, doi:10.1039/CT9079102001 (1907).

  65. 65.

    Ferris, J. P., Hill, A. R., Liu, R. H. & Orgel, L. E. Synthesis of long prebiotic oligomers on mineral surfaces. Nature 381, 59–61, doi:10.1038/381059a0 (1996).

  66. 66.

    Lv, K. L., Perriman, A. W. & Mann, S. Photocatalytic multiphase micro-droplet reactors based on complex coacervation. Chem Commun 51, 8600–8602, doi:10.1039/C5CC01914A (2015).

  67. 67.

    Aumiller, W. M. Jr., Davis, B. W., Hatzakis, E. & Keating, C. D. Interactions of macromolecular crowding agents and cosolutes with small-molecule substrates: effect on horseradish peroxidase activity with two different substrates. The journal of physical chemistry. B 118, 10624–10632, doi:10.1021/jp506594f (2014).

  68. 68.

    Hud, N. V., Cafferty, B. J., Krishnamurthy, R. & Williams, L. D. The Origin of RNA and “My Grandfather’s Axe”. Chem Biol 20, 466–474, (2013).

  69. 69.

    VanDerVoort, P. & Vansant, E. F. Silylation of the silica surface a review. Journal of Liquid Chromatography & Related Technologies 19, 2723–2752, (1996).

  70. 70.

    Meijer, J. M. et al. Self-Assembly of Colloidal Cubes via Vertical Deposition. Langmuir 28, 7631–7638, doi:10.1021/la3007052 (2012).

  71. 71.

    Schneider, C. A., Rasband, W. S. & Eliceiri, K. W. NIH Image to ImageJ: 25 years of image analysis. Nat Methods 9, 671–675, doi:10.1038/nmeth.2089 (2012).

Download references


This work was supported by NASA Exobiology program, grant number NNX13AI01G. The authors thank Daniel Veghte and Sarah Sihvonen from Freedman group for clay samples and helpful discussions.

Author information


  1. Department of Chemistry, Pennsylvania State University, University Park, Pennsylvania, 16802, USA

    • Fatma Pir Cakmak
    •  & Christine D. Keating


  1. Search for Fatma Pir Cakmak in:

  2. Search for Christine D. Keating in:


F.P.C. and C.D.K. analyzed the data and designed the experiments, F.P.C. carried out the experiments. F.P.C. and C.D.K. wrote the manuscript.

Competing Interests

The authors declare that they have no competing interests.

Corresponding author

Correspondence to Christine D. Keating.

Electronic supplementary material


By submitting a comment you agree to abide by our Terms and Community Guidelines. If you find something abusive or that does not comply with our terms or guidelines please flag it as inappropriate.

Creative Commons BY

Open Access This article is licensed under a Creative Commons Attribution 4.0 International License, which permits use, sharing, adaptation, distribution and reproduction in any medium or format, as long as you give appropriate credit to the original author(s) and the source, provide a link to the Creative Commons license, and indicate if changes were made. The images or other third party material in this article are included in the article’s Creative Commons license, unless indicated otherwise in a credit line to the material. If material is not included in the article’s Creative Commons license and your intended use is not permitted by statutory regulation or exceeds the permitted use, you will need to obtain permission directly from the copyright holder. To view a copy of this license, visit