Enzyme-based electrochemical biosensors are an inspiration for the development of (bio)analytical techniques. However, the instability and reproducibility of the reactivity of enzymes, combined with the need for chemical reagents for sensing remain challenges for the construction of useful devices. Here we present a sensing strategy inspired by the advantages of enzymes and photoelectrochemical sensing, namely the integration of aerobic photocatalysis and electrochemical analysis. The photosensitizer, a bioinspired perfluorinated Zn phthalocyanine, generates singlet-oxygen from air under visible light illumination and oxidizes analytes, yielding electrochemically-detectable products while resisting the oxidizing species it produces. Compared with enzymatic detection methods, the proposed strategy uses air instead of internally added reactive reagents, features intrinsic baseline correction via on/off light switching and shows C-F bonds-type enhanced stability. It also affords selectivity imparted by the catalytic process and nano-level detection, such as 20 nM amoxicillin in μl sample volumes.
The use of enzymes for chemical analysis is well documented. Horse radish peroxidase (HRP), a typical example, has been employed either as a selective catalyst to transform an analyte into an easily detectable product1,2 or as an enzymatic label in immunosorbent assays and related techniques3,4,5. The advantage of enzymes is their catalytic signal amplification, which translates into high sensitivity and low limits of detection (LOD). Enzyme-based reagents, in combination with a cost efficient and straightforward electrochemical detection method could lead to portable, selective and sensitive sensors6,7 not unlike the widely used personal glucose meters8.
Several research groups have advanced over last three decades the electrochemical detection of phenols at HRP modified electrodes9,10,11 as well as the use of HRP and alkaline phosphatase (ALP) as enzyme labels in electrochemical immunoassays12,13,14. However, despite these efforts and commercial interests, progress in commercialization of electrochemical biosensors remains slow15,16,17. The reasons include the complexity of fabrication of sensing elements, the thermal and chemical instability of enzymes during fabrication, sterilization and storage18, the reproducibility of enzyme activity and immobilization procedures, as well as challenges related to field-use of reagents, for example unstable hydrogen peroxide (H2O2). Thus, sensitive yet robust, renewable reagents and simple, reliable detection approaches are needed.
The elegant idea of using light to activate the chemical conversion of an analyte has been recently introduced in the field of electrochemical analysis19,20. Chronoamperometry using disposable, screen-printed electrodes (SPE) yields a detection platform similar to that of glucose meters. In the case of so-called photo-electrochemical sensors an analytical signal (photocurrent) is triggered only by light and thus it can be cleanly distinguished from background by simply switching the light off. Advantageously, relatively stable reagents could be photoactivated to start a measurement. For example, an illuminated semiconductor can become a strong electron acceptor, capable to oxidize an organic compound and exchange electrons with an electrode21.
Here, we describe a detection paradigm based on the reliability of photoelectrochemical detection and the principles of enzyme detection, that is, catalytic signal amplification, but translated into a bioinspired catalyst that needs only air and light to function. The active, bioinspired enzyme replacement is a Type II molecular photosensitizer which, under visible light illumination generates reactive singlet delta oxygen, 1O2, which, in turn triggers the appearance of a photocurrent due to its, or its daughter species (Reactive Oxygen Species, ROS) reactions with analytes such as amoxicillin. In addition, we show that photosensitizers such as Pheophorbide A coupled to biomolecules allow a singlet oxygen based DNA–DNA recognition with on-demand reactivity controlled by switching the light on/off.
Enzymatic and photosensitizer electrode mechanisms
Figure 1 illustrates the conceptual parallel between the enzymatic and photosensitizer electrode mechanisms. Specifically, an oxidant, viz H2O2 or O2 interacts with a catalyst, viz HRP or a photosensitizer yielding highly reactive intermediates, namely a ferryl heme or 1O2, respectively. These intermediates, in turn, rapidly oxidize a substrate, for example hydroquinone (HQ) or another appropriate electron donor in the case of HRP22. The HRP oxidant is the iron-oxo core, a classical electron plus proton abstractor, to yield from HQ water and the oxidized product, benzoquinone (BQ). The BQ is electrochemically reduced at a polarized electrode to regenerate HQ thus completing a catalytic redox cycle (Fig. 1a,b). Alternatively, a bio- or photo-catalyst could irreversibly convert an initially redox-inactive reagent into a redox-detectable product, quantifiable electrochemically (Fig. 1c). A lower sensitivity is noted for pathway 1c relative to the redox cycling schemes 1a and 1b, but this scheme's simplicity and low background renders it popular for immunoassays. In contrast, the redox schemes dependency on electron donors, for example phenols makes them useful for their quantification9,10,11. The proposed enzymatic-like approach relies on catalysed photo-transformation of dissolved, aerobic 3O2 in the reactive, short-lived 1O2. Advantageously, this approach needs neither H2O2, unlike HRP-based techniques (Fig. 1a,b) nor p-aminophenyl phosphate, unlike ALP-based ones (Fig. 1c).
Structural and spectroscopic features of the photosensitizer
The proposed, chemically robust perfluorinated phthalocyanine complex F64PcZn (Fig. 2a) produces 1O2 in a relatively high quantum yield23,24,25. Unlike the protio phthalocyanine, H16PcZn, F64PcZn is stable in the presence of 1O2 and daughter, oxygen-centered species and other radicals26,27. The bulky i-C3F7 groups of F64PcZn effectively protect this molecule from aggregation and facilitate its dissolution in organic solvents such as ethanol. Site isolation is an important feature since aggregation, exhibited by the fluorinated F16PcZn diminishes the 1O2 yield due to the shortening of the excited states lifetimes and/or inefficient intersystem crossing. In addition, the aromatic fluorines of F16PcZn are subject to nucleophilic attack, including from some ROS species thus rendering this molecule less viable for 1O2 photocatalysis28. In contrast, attempts to detect nucleophilic substitutions at the 8 β C-F positions of F64PcZn have not succeeded thus far, due at least in part to the steric hindrance afforded by the eight adjacent α bulky i-C3F7 groups. This observation further recommends the proposed F64PcZn for sustained 1O2 production.
In summary, the F64Pc scaffold affords chemically and thermally stable yet photoreactive complexes26,27 features that led to its choice. Furthermore, the need for solid-state catalysts using the F64Pc scaffold led to the exploration of its support on materials, including TiO2 (ref. 29). F64PcZn was deposited in 0.5 to 3 wt% on TiO2, a carrier matrix with a 21 nm primary particle size and 35–65 m2 g−1 surface area. The diffuse reflectance ultraviolet–visible spectrum of the hybrid material, TiO2-F64PcZn, exhibited the characteristic Q-band30,31 of phthalocyanines in the 600–700 nm range and absorbance below 400 nm, attributed to a combination of Soret bands and the intrinsic absorbance of TiO2 (Fig. 2). The Q-band is relatively broad, but centered at the same position as that of F64PcZn in solution. The 655 nm wavelength of a common diode laser pointer essentially matches the Q band of TiO2-F64PcZn, a material that was shown to produce 1O2 using visible and filtered red light29 Thus, a photoelectrochemical response of F64PcZn-TiO2 deposited on screen printed electrodes, abbreviated SPE|TiO2-F64PcZn should be absent in the absence of red-light exposure, but could be measurable under illumination. Importantly, dark measurements automatically reveal the actual baseline position, leading to an efficient and straightforward way for baseline correction even in the presence of analytes.
Oxygen- and electron-based photocatalysis
The essential role of O2 for substrate detection using the photodynamic effect observed for F64PcZn in solution24,25 and ex vivo23,32, was confirmed by comparing photocurrents obtained in an air-saturated buffer with those obtained under an inert N2 atmosphere (Fig. 3). The photocurrents were completely suppressed on N2 purges, whether HQ was present or not, but recovered completely on admission of air, consistent with a Type II mechanism and the high 1O2 quantum yield (ΦΔ∼0.6 in acetone, methanol) previously reported for F64PcZn23,24,25,32. Intriguingly, for SPE|F64PcZn the anaerobic photocurrent (under N2) exhibits a sign reversal in the presence of HQ, suggesting a direct electron transfer from HQ to F64PcZn and, eventually to the electrode, in agreement with a recent report on the direct photoreduction of F64PcZn by an electron donor in strictly oxygen-free conditions30. In other words the photo-oxidation of HQ, which is atom-based (1O2) in the presence of air, shifts to electron based in O2 absence: the SPE accepts electrons from the reduced, anionic F64PcZn thereby regenerating continuously the original SPE|F64PcZn. This mechanism is specific only to SPE|F64PcZn since the lack of electronic connection between the SPE surface and F64PcZn in SPE|TiO2-F64PcZn precludes the appearance of a photocurrent in the absence of O2.
The photo-anaerobic signal observed for SPE|F64PcZn, given the extreme electron deficiency of the perfluorinated F64Pc scaffold might also be considered the basis for a versatile anaerobic sensor application, but this research direction is not pursued in this work.
Dependency on electrodes and applied potentials
Variations in photocurrents function of the applied potential were investigated by linear sweep voltammetry under light-chopped illumination. The SPEs were subjected to alternating illumination and dark periods of 50 s each, with and without the photosensitizer (Fig. 4).
The bare SPE and the SPE|TiO2 showed no photocurrent response either in the absence or presence of HQ (Fig. 4a,b). In contrast, a photocurrent response was observed for SPE|F64PcZn and SPE|TiO2-F64PcZn (Fig. 4c,d) due to the formation of 1O2 and its subsequent reduction at the electrode surface (Fig. 1f). Higher values of the photocurrent are noted in the presence of HQ due to its redox cycling (Fig. 1d). Noteworthy, at similar F64PcZn loadings and in the absence of HQ the response of SPE|F64PcZn is higher relative to that of SPE|TiO2-F64PcZn. Moreover, when 10 μM HQ is added, the SPE|TiO2-F64PcZn photocurrent increases 20-fold, while the response of SPE|F64PcZn is unchanged. More detailed amperometric measurements at higher HQ concentrations revealed that SPE|F64PcZn is 50-fold less sensitive to HQ relative to SPE|TiO2-F64PcZn (Supplementary Fig. 1). These observations could be rationalized considering that 1O2, the photocurrent trigger has a limited lifetime in water, namely 3.5 μs (ref. 33). Taking into account the 2 × 10−5 cm2 s−1 diffusion coefficient of O2 in water 1O2 can diffuse only about 200 nm, commensurate with the thin F64PcZn layer of SPE|F64PcZn. In contrast, since the TiO2-F64PcZn layer of SPE|TiO2-F64PcZn is obviously more voluminous, a portion of the F64PcZn is outside the 1O2 diffusion radius and thus the 1O2 it produces decays before reaching the electrode, leading to a lower value of the photocurrent. However, once HQ is present the more stable but redox active BQ occupies a much larger diffusion volume and thus all F64PcZn of SPE|TiO2-F64PcZn (same loading as SPE|F64PcZn) contributes now to the photocurrent. The significantly higher activity of SPE|TiO2-F64PcZn versus SPE|F64PcZn is due to the highly dispersed state of F64PcZn supported on nano-size TiO2, as opposed to it being present as a thin film.
The expected photoinactivity of semiconducting TiO2 under low-energy, 655 nm illumination was verified by testing the similar SPE|SiO2-F64PcZn electrode prepared from insulating SBA-15 SiO2. The test device exhibited roughly the same activity as SPE|TiO2-F64PcZn, thus verifying TiO2 exclusive role as a supporting matrix29 (Supplementary Fig. 2). Coatings of SiO2-F64PcZn, however are non-uniform and mechanically unstable and thus have not been used further.
Photocurrents in the presence and absence HQ depended quasi-linearly on the photosensitizer loading for both SPE|TiO2-F64PcZn and SPE|F64PcZn (Supplementary Fig. 3), as expected for catalytic processes. A higher linearity is obtained for the matrix supported F64PcZn electrodes, consistent with a load-independent reactivity-type imparted by a non-aggregating, single-site catalyst condensed as thin films or supported on oxidic materials. This observation validates the anticipated, beneficial role of steric hindrance in insuring maximum photophysical activity. The photocurrent plateau observed for SPE|F64PcZn suggests that thicker F64PcZn films provide diminishing electron transfer ability, again consistent with steric site-isolation and lack of intermolecular electron coupling, as additionally evidenced by the EPR of magnetically isolated, isostructural F64PcCu34.
Photocurrents dependency on light sources
Amperometry measurements were conducted using different 665 nm laser power settings (Supplementary Figs 4 and 5). The photocurrent increase was steep up to about 20 mW, but tended to diminish when the power exceeded 50 mW. Standard LED lamps emitting 2,100 and 3,000 millicandelas at 660 nm provided a response equivalent to laser powers of 1.2 and 1.7 mW or 15.6 and 22.4% of the sensitivity at 30 mW, respectively.
Detection of phenolic analytes
HRP was reported to be a promising reagent for the detection of phenols through their oxidation to redox active derivatives9,10,11,35,36. A Type II photosensitizer is now used for the same purpose, therefore a detection mechanism is proposed (Fig. 1b,e). This proposal is consistent with the reported pathway for photocatalytic degradation of phenol37,38 and phenolic derivatives39,40, including pollutants and pharmaceuticals41,42.
Amoxicillin, a β-lactam antibiotic containing a phenolic moiety was used to test the efficiency of the proposed detection strategy. Similar to HQ, amoxicillin triggers a potential-dependent rise of the photocurrent (Fig. 5), which remains constant beyond a potential of around −0.1 V versus SCE. By analogy with HQ, a 1O2-mediated photo-oxidation of amoxicillin yielding a redox active product may occur, followed by the reduction of this product at the electrode. This mechanistic proposal is based on the reported reaction of 1O2 with the 4-hydroxyphenyl moiety of amoxicillin via a [2+2] cycloaddition which yields an unstable 1,4-endoperoxide that, in turn decays to the corresponding p-peroxyquinol38,43. A minor product, a 3,4-dihydroxyphenyl derivative can be additionally formed, similar to the oxidation of tyrosine by 1O2 (ref. 44).
How selective is the proposed detection for phenols? Ampicillin, which lacks the aromatic hydroxyl group of amoxicillin, as well as benzylpenicillin, nafcillin, and 6-aminopenicillanic acid produced no noticeable photocurrents even in concentrations as high as 100 μM (Table 1 and Supplementary Fig. 6). Several phenols, were evaluated next (Supplementary Table 1). Setting hydroquinone to 100, the relative sensitivities are: 4-aminophenol, 113; 2-chlorophenol, 44; bisphenol A, 39; amoxicillin, 32. Surprisingly, only a minor response was observed for 4-methylphenol, 1. Phenol, bisphenol A, 4-nitrophenol and 2-chlorophenol have longer response times, 50–100 s, in comparison to HQ, 10 s, likely due to their slow reactions with 1O2 (ref. 45). Reaction rates increase with the pH45, a change to pH 12 results in both a fast response, 5 s, as well as a fivefold increase in sensitivity, as demonstrated for phenol and bisphenol A (Supplementary Table 1).
In contrast to phenols, ascorbic acid is an example of a compound that can rapidly but irreversibly react with singlet oxygen46. The lack of redox cycling limits its photocurrent response. Indeed, the sensitivity of the proposed electrode to HQ is three orders of magnitude higher compared to that for ascorbic acid, as evidenced by the appearance of only a minor photocurrent response even when the concentration of ascorbic acid exceeds 100 μM (Supplementary Table 1). Notably, ascorbic acid does not suppress the response of HQ at a 1:1 molar ratio. The photocurrent intensity is halved only if ascorbic acid is present in 100-fold excess. Applications for the detection of phenols in the presence of ascorbic acid, for example in fruits and beverages are thus possible since the phenols are always present in excess47.
Plots of the photocurrent for amoxicillin as a function of its concentration reveal that the sensitivity was 0.14 A M−1 cm−2 in the low concentration range, corresponding to the limit of detection (LOD) 22 nM, calculated from the 3s.d. value of the background signal (s.d.=0.13 nA, n=16) (Fig. 6). The photocurrents for HQ were about three times higher compared to amoxicillin, possibly because of the slower photo-oxidation kinetics for amoxicillin compared to HQ (Supplementary Fig. 7). The sensitivity for HQ was 0.41 A M−1 cm−2 with a LOD of 12 nM.
Notably, the LOD values for both amoxicillin and HQ were about two orders of magnitude lower compared to a recently reported system using iron phthalocyanine (Type I photosensitizer) designed for dopamine detection48, and one-two orders of magnitude lower compared to HRP-modified electrodes used for the detection of phenolic compounds9,10,35,36. Similar, favourable results are noted following a comparison with previously published phenolic analytes (Supplementary Table 2), as well as with amoxicillin determinations using different electrochemical methods (Supplementary Table 3).
A direct comparison between F64PcZn and HRP modified electrodes provides more insights into the proposed method. To our knowledge, the detection of amoxicillin using an enzymatic biosensor has not been reported. Thus, a SPE|TiO2-HRP electrode, analogous with SPE|TiO2-F64PcZn was constructed. The HRP-based electrode detected HQ with sensitivity similar to that of TiO2-F64PcZn (Fig. 7), but it did not detect amoxicillin, substantiating the advantages of the catalytic, 1O2-mediated detection strategy.
The favourable sensitivity reported above is dependent on the signal-to-noise ratio of the detection method. The photocurrent of the SPE|TiO2-HRP was observed to fluctuate on the addition of H2O2 when low concentrations of HQ were measured (Fig. 8), consistent with known H2O2 problems49. Mitigation attempts by disconnecting and reconnecting the electrode exacerbated the baseline instability. A second remedy was tried by maintaining the reaction volume strictly constant. Hence, HQ was introduced by removing 20 μl from the total volume (100 μl) and returning the same volume of HQ solution also containing H2O2. Thus, measurements were performed continuously without switching off the cell or affecting noticeably the concentration of H2O2. The addition of 0.1 μM HQ after 20 min of the baseline stabilization elicited no clear response (Fig. 8). The lowest concentration detected was 0.2 μM although the sensitivity of the electrode, 0.39 A M−1 cm−2 was similar to that of SPE|TiO2-F64PcZn. The extrapolation of the baseline beyond the time the sample is introduced, however, is problematic rendering the LOD values uncertain.
In this respect, the strategy we suggest presents a distinct LOD advantage since switching off the light reveals the baseline current under the experimental measuring conditions, thereby affording a simple, straightforward correction if necessary. Moreover, while the photoelectrochemical and HRP-based approaches reveal similar selectivity patterns (Supplementary Table 1), the phthalocyanine, unlike HRP is stable at elevated pH values. As mentioned above, a higher pH favours the reaction of phenols with 1O2 (ref. 45), and might be encountered when measuring analytes in basic wastewaters. In general, enzymes function only within narrow pH ranges, a condition which is less restrictive in the case of chemically robust photosensitizers.
Photosensitizers as labels of biomolecules
The selectivity based on the specific reactions of 1O2 could be enhanced by attaching photosensitizers to supports that exhibit binding selectivity. To demonstrate this point, a commercially available oligonucleotide of 15 bases labelled by Pheophorbide A, a chlorophyll-derived, well-known photogenerator of singlet oxygen50,51 apoporphyrin was used, consistent with its F64PcZn-related ex vivo reactivity32. The oligonucleotide sequence was chosen to be complementary with microRNA-21, an important marker for several types of cancer and cardiovascular diseases52. The electrodes were modified by a DNA probe with the complementary sequence, while a non-complementary DNA probe of the same length was used as a blank control.
As shown in Fig. 9, the complementary oligonucleotide elicited a clear photocurrent response, but only a very small photocurrent was observed for the non-complementary sequence. The photocurrents, reproducible within a series of four electrodes had an average value of 316 pA (s.d.=11 pA, n=4), a number that exceeded ∼12 times the 25 pA (s.d.=13 pA, n=4) average photocurrent in blanks. The signals, however, are time-dependent, dropping by 40% after four sequential illuminations of 30 s (Supplementary Fig. 8). The decay was likely due to the oxidative DNA cleavage and, possibly the photodegradation of the photosensitizer. Note that the dark photocurrent remained constant for 40 min after the electrode incubation in the measuring buffer (Supplementary Fig. 8). Thus, the signal decay was likely not due to the dissociation of the labelled oligonucleotide from the electrode surface. Nevertheless, the decay of the photocurrent, which reached its maximum after 5 s of illumination is not critical for the one-time detectability of the complementary oligonucleotide due to this fast response of the sensor.
The use of enzymes for chemical analysis is reaching maturity. Photosensitizers generating 1O2 have been explored and exploited in the fields of organic synthesis, medical photodynamic therapy and others, but not yet in the field of chemical sensors53,54. The proposed analogy between the photo-catalytic and enzymatic detection schemes, Fig. 1, might be the basis for new directions of exploration of 1O2-generating photo-catalytic materials as chemical sensors.
The high reactivity of 1O2 and its ROS daughters, however, limits the use of photocatalytic materials due to photosensitizers degradation and thus low turnover numbers54. This is not surprising considering that C–H bonds containing photosensitizers are being attacked by the 1O2 and ROS they produce. Moreover, the oxidation of analytes may also generate reactive species, including radicals, an additional source of sensor degradation.
The photosensitizer photo-degradation is mitigated by using a fully fluorinated Zn phthalocyanine complex, F64PcZn, an efficient yet stable 1O2 generator26,27 in solution and in the solid state. The manufacture of electrodes containing F64PcZn revealed that robust, ROS and redox processes inactivation-resistant sensors can be produced. The bulky F64Pc organic scaffold, complexed by a closed-shell metal ion like Zn2+ precludes deactivating aggregation, exhibits reversible electron addition and resistance to radical, electrophilic and nucleophilic attacks27.
Electronic transfers to/from the sensor are thus feasible while the interactions of electrodes with analyte species occur without baseline interference. The latter process is possible since only light switching triggers the appearance of analyte products, the dark photocurrents being obtained from a chemical composition-invariable environment. Compared with enzymatic detection, significantly higher signal-to-noise ratios are generally observed, while selectivity based on the type of chemical oxidation represents an additional bonus.
The proposed strategy compares favourably with HRP-based detection for a series of phenols, including pharmaceuticals bearing the phenol functionality. The analyte chosen as an example, amoxicillin, is the most used antibiotic55, but also contaminates hospital trash and urban wastewaters and is therefore a marker in environmental management and pollution control56. Amoxicillin and other phenols' selective detection suggests that the direct, ene reactivity of 1O2 operates, as noted previously for phenol38 and dominates the selective sensing process. The shuttle of electrons between a site of 1O2 production/reactivity and an electrode occurs for both SPE|TiO2-F64PcZn and SPE|F64PcZn electrodes that detect redox-active products, but the nano-dispersed TiO2-F64PcZn is more effective due to its high surface area and spatial distribution of F64PcZn in the large bulk volume of the support. The sensing efficiency can be understood and tuned using classical catalysis principles.
Catalyst robustness, structural modifications favouring single-site isolation, loading degree, light intensity, dark baseline corrections, surface area and particle sizes of supports and so on, could be used to optimize performance. The kinetics of the 1O2-mediated oxidation of an analyte could be further tuned by modifying the reaction conditions such as temperature and pH, as shown for phenols. The large variation of pH, an important parameter for optimizing sensors' sensitivity and selectivity, is unavailable in the enzymatic detection scheme.
Molecular photosensitizers could also be used as labels for biorecognition/affinity assays even if somewhat unstable, such as Pheophorbide A since the signal decay takes minutes while detection occurs seconds after the catalyst is photoactivated. The life-time of 1O2 suggests a diffusion distance of about 200 nm and thus the label itself does not need to contact an electrode to produce an analytical response. Application of this detection scheme, however, is rather limited by the single-use type of the sensors due to the response decay in a sequence of repeatable measurements. While electroactive compounds (for example, ferrocene) could still be useful as labels in case of short stranded DNA, they cannot provide an efficient and generic solution for affinity sensors due to the rapid charge transfer rate–distance decay57,58 that results in poor signals for biomolecules, whose typical size is a few nanometers.
As noted above, the redox cycling afforded by HQ results in remedial signal amplifications due to electrons shuttling between the electrode and the 1O2 producing photo-catalyst, suggesting opportunities for electrochemical microarrays and washing-free immunosensors59.
In conclusion, robust, perfluorinated molecular photosensitizers, resistant chemically yet reactive, have been shown as proof-of-principle efficient enzymes mimics for electrochemical (bio)sensing applications, while favourably enhancing the useful feature of the enzymatic detection mechanism, namely the catalytic formation of an easily detectable product and redox cycling. A Type II photosensitizer generates photocurrents using air oxygen without the need to add any supplementary reagents.
The perfluorination of the sensitizer insures its functional resilience as well as long term stability vis-à-vis the reactive oxygen and other species it may generate. The use of catalytic photosensitizers instead of enzymes for analytical sensing offers several advantages, including: chemical and thermal stability; on-off control of sensing by on-off light switching; facile dark baseline monitoring and adjustments; invariable structural and reactivity properties of photocatalytic, well-defined metal complexes; comparative simplicity and low preparation price; facile chemical modification and functionalization, attachment to biomolecules and surfaces.
The bioinspired molecules, subject to chemical modifications, coupled to biomolecules may allow conjugates to function in the same way as fluorescent dye- and enzyme-labelled (for example, HRP-labelled) reagents, but affording an additional, on-demand reactivity controlled by simply switching the light. An enhanced degree of flexibility in the design of biorecognition elements and the functionalization of sensor surfaces is envisioned. The present example of a bioinspired strategy of replacing an enzyme with synthetic components for analytical purposes could be useful for developing applications ranging from chemistry to biology and environmental monitoring.
Perfluorophthalocyanine Zn, F64PcZn was synthesized and characterized as described earlier24 Briefly, perfluoro-(4,5-bis-isopropyl)phthalonitrile was prepared from perfluorophthalonitrile and perfluoropropene and reacted with Zn acetate. The obtained product was purified chromatographically and recrystalized twice from acetone. The 19F NMR and UV–vis spectra were identical with the literature data.
Titanium dioxide, TiO2 (Aeroxide P25) and silicon dioxide, SiO2 (AEROSIL OX 50) were obtained from Evonik Inorganic Materials (USA).
Before impregnation with F64PcZn, SiO2 and TiO2 were dried at 100 °C for 2 h. After dissolving F64PcZn in 10 ml of absolute ethanol, either SiO2 or TiO2 were added to this solution. The ethanol was evaporated under vacuum and the impregnated materials were dried at 100 °C for 6 h. Loadings of 0.5–3.0% wt F64PcZn were confirmed spectrophotometrically by back extracting the phthalocyanine from the impregnated materials with acetone (Soxhlet) until the oxide appeared white and no phthalocyanine was observed via reflectance ultraviolet–visible spectroscopy. TiO2 containing 3 wt % F64PcZn was used in all experiments, if not mentioned otherwise.
For the impregnation of TiO2 with HRP, TiO2 was suspended in a solution of 0.125 mM HRP in 10 mM HEPES pH=7 buffer and the mixture was agitated overnight on a rotatory shaker. The suspension was centrifuged and the pellet washed three times with 10 mM HEPES pH=7 buffer and dried at room temperature for 8 h. The resulting powder was refrigerated before use. A loading of 1.06 μmol g−1 (4.6 wt %) was calculated from the concentration of HRP in the supernatant collected after adsorption. The supernatants of washing solutions did not contain any noticeable amount of HRP.
Oligonucleotides were obtained from Eurogentec (Belgium). Their structures and purity were confirmed by mass-spectrometry. Sequences of the oligonucleotides were as follows: probe 1 (complementary): 5′-HS-(CH2)6-tagcttatcagactgatgttga-3′; probe 2 (non-complementary): 5′-HS-(CH2)6-tagcttatgtgtaccctgtcag-3′; oligonucleotide labelled by Pheophorbide A: 5′-Pheo-tcaacatcagtctga-3′. A detailed description of the procedures used for the modification of electrodes by the probes and detection of the labelled oligonucleotides is provided in the Supplementary Methods.
Amoxicillin of 99.4% purity was obtained from TCI Europe (Belgium), HQ of 99.9% purity was purchased from Acros Organics (Belgium). Other phenolic compounds were 98% purity or better and obtained from different suppliers. L-Ascorbic acid of 99.5% purity was obtained from Sigma-Aldrich (Belgium). Ultrapure water was used for all experiments.
The electrochemical measurements were conducted using a μAutolab III (Metrohm-Autolab BV) instrument. Data for calibration curves were obtained using PalmSens3 (PalmSens BV) instrument. Ultraviolet–visible diffuse reflectance spectra were measured using an Evolution 500 double-beam spectrophotometer equipped with RSA-UC-40 DR-UV integrated sphere (Thermo Electron Corporation) or a Cary 5000 instrument.
A diode laser pointer operating at 655 nm (Roithner Lasertechnik, Austria) was adjusted to 30 mW power using a light power meter. A power supply was programmed to switch on and off the light beam at given time intervals.
Screen-printed carbon electrodes (SPE) were purchased from DropSens (Asturias, Spain).
The modification of electrodes by F64PcZn to give SPE|F64PcZn was performed by depositing a 5 μl drop of 0.3 mg ml−1 of F64PcZn solution in ethanol on SPEs and letting the solvent evaporate.
The SPE|TiO2-F64PcZn were manufactured by adding a 5 μl drop of an aqueous suspension containing 10 mg ml−1 TiO2-F64PcZn on the working electrode surface of SPEs and allowing the water to evaporate completely at room temperature.
Measurements with SPE were performed in a drop of 80 μl. Measuring buffer consisted of 0.1 M KCl and 20 mM KH2PO4 (pH=7) dissolved in ultrapure water. A saturated calomel electrode (SCE, Radiometer, Denmark) was used as an external reference electrode whenever necessary. The quasi-reference electrode of SPEs had the potential of +0.04 V versus SCE in the measuring buffer. All potentials in the text are given versus SCE. To study the effect of oxygen, a tightly closed three electrode cell was used with SPE, SCE, and a glassy carbon rod as the working, reference and counter electrodes, respectively. The beam of the diode laser was directed to the working electrode surface through the glass wall of the cell. Some, constant power loss was noted due to the glass wall absorption.
All data is available from the authors on reasonable request.
How to cite this article: Trashin, S. et al. Singlet oxygen-based electrosensing by molecular photosensitizers. Nat. Commun. 8, 16108 doi: 10.1038/ncomms16108 (2017).
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Evonik is thanked for providing samples of silicon and titanium oxides. Support from the National Science Foundation (SMG) for a portion of this work is gratefully acknowledged. FWO and UAntwerpen (BOF) are acknowledged for financial support.
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Nano Convergence (2018)