Marjorie
Yon
,
Claire
Pibourret
,
Jean-Daniel
Marty
* and
Diana
Ciuculescu-Pradines
*
Laboratoire IMRCP, CNRS UMR 5623, Paul Sabatier University, 118 route de Narbonne, 31062 Toulouse, France. E-mail: marty@chimie.ups-tlse.fr; ciuculescu-pradines@chimie.ups-tlse.fr
First published on 7th September 2020
The possibility to easily and rapidly assess the presence of Gd3+ ions in solution is of paramount importance in many domains like magnetic resonance imaging. In that context, the use of easy to implement colorimetric sensing probes based on gold nanoparticles (AuNPs) is of special interest. Herein, AuNPs functionalized with a commercial bis(p-sulfonatophenyl)phenyl phosphine ligand (BSPP) (AuNP@BSPP), bearing negatively charged sulfonate groups are used as a colorimetric sensing probe. The addition of Gd3+ ions onto these NPs was studied through UV-visible absorbance measurements, Quartz Crystal Microbalance with Dissipation monitoring (QCM-D) and transmission electron microscopy and compared with citrate covered AuNPs. We evidenced interactions between the Gd3+ ions and their water rich coordination sphere and sulfonate groups on the surface of AuNP@BSPP via electrostatic interactions and hydrogen bonding. These interactions induce the reversible aggregation of AuNP@BSPP in the presence of concentrations of Gd3+ ions at a μM level. We took advantage of this phenomenon to develop a simple and fast bench colorimetric assay for the detection of free Gd3+ ions, based on the determination of a flocculation parameter thanks to UV-visible measurements. Limits of detection and quantification were found equal to 0.74 μM and 4.76 μM of Gd3+ ions, respectively, with a high sensitivity that competes with conventional methods used for lanthanide detection.
In that context the use of gold nanoparticles (AuNPs) as colorimetric sensing probes have piqued much interest3 in addition to their application in biomedical imaging.4 AuNPs are still today one of the largest studied inorganic colloids, due to their interesting photo-physical properties, easy preparation and functionalization.5 The ability to detect, selectively and quantitatively, metal ions relies on the interactions of metal ions with these AuNPs that modify the dielectric properties of the ligand shell and eventually induce aggregation. Both phenomena responsible for the change of optical properties of colloidal solutions, can be further related to the concentration of ions in solution. The affinity and selectivity towards metal ions require to have access to AuNPs with both a well-controlled morphology (size and shape) and the suitable nature of the ligands present at their surface. However, available synthetic methods are still unsuited to have direct access to such NPs due to three main limitations: (i) the control of NP core size and shape often requires stringent growth conditions relying on the use of specific solvents, and reducing and functionalizing agents, (ii) a purification step is needed between the synthesis of the core and the surface modification, and (iii) the surface modification by ligand exchange or chemical reaction is often limited and is time-consuming requiring special design of the ligands and precise control of the functionalization process involving frequently inadvertent aggregation of the particles.
Here in order to have access to AuNPs with a controlled morphology and functionalization to be used as colorimetric probe, we decided to start from 20 nm AuNPs synthesized by the Turkevich and Frens method,6,7 denoted as AuNP@citrate. Despite the convenience and reproducibility of this synthesis, the resulting colloidal solution displays poor stability due to the weak binding of the citrate ions to the gold surface. Bis(p-sulfonatophenyl)phenylphosphine (BSPP) is added to lead to more stable negatively charged modified AuNPs,8 denoted as AuNP@BSPP (Fig. 1).
Despite the large use of AuNP@BSPP, there is no study concerning their behavior in the presence of lanthanide ions, so far. We demonstrate in this article the high sensitivity of the optical properties of these NPs to the addition of Gd3+ ions. UV-visible spectroscopy and quartz crystal microbalance with dissipation monitoring (QCM-D) measurements enable the understanding of the mechanism responsible for this phenomenon. Finally, we took advantage of the behavior of AuNP@BSPP to validate a highly sensitive colorimetric test for the detection of gadolinium ions. We illustrate this method to quantify free Gd3+ ions present in the colloidal systems obtained from polymers and Gd3+ ions, and compare the results obtained with the ones issued from ICP-MS analysis.
UV-visible absorption spectra of AuNP@citrate and AuNP@BSPP solutions are shown in Fig. 2A. In the case of AuNP@citrate, a surface plasmon resonance band is clearly visible with a maximum absorbance at 522 nm.5 An estimation of the diameter of the AuNPs can be obtained from the ratio of the absorbance measured at the maximum of the peak to the one at 450 nm as detailed in the supporting information (ESI Fig. S1†).12 From this, an average diameter of 17 nm could be estimated in agreement with the size found by transmission electron microscopy (TEM) (ESI Fig. S2†). A slight increase of the maximum absorbance of the surface plasmon resonance peak and a red shift from 522 to 523 nm is observed upon addition of the phosphine ligand due to changes of the dielectric environment around nanoparticles.5,13 An average diameter of 17.2 ± 4.0 nm was measured from TEM images (Fig. 2B) in good agreement with pristine AuNP@citrate. In addition, the efficiency of ligand exchange was assessed from dynamic light scattering (DLS) and by sedimentation field-flow fractionation (SdFFF) measurements (see Fig. S3 and S4 in ESI†). An intensity-averaged hydrodynamic diameter equal to 31 ± 11 nm and 33 ± 11 nm was obtained for the AuNP@citrate and AuNP@BSPP, respectively (inset in Fig. 2A). The growth or aggregation of the NPs during the ligand exchange process can therefore be excluded. Zeta potentials of AuNP@citrate and AuNP@BSPP solutions are −35 ± 3 mV and −40 ± 5 mV, respectively, evidencing, as expected, a negative surface charge of the NPs (see ESI Fig. S5†).
Fig. 2 (A) UV-visible spectra and intensity-averaged hydrodynamic diameter distribution (inset) estimated from dynamic light scattering measurements of AuNP@citrate (red curve) and AuNP@BSPP (black curve). A small peak is observed in DLS at sizes lower than 5 nm due to rotational diffusion of particles.14 (B) Transmission electron microscopy image of AuNP@BSPP and the respective size distribution histogram (inset). |
Fig. 3 (A) Photographs showing the color response of AuNP@citrate (first line) and of AuNP@BSPP (second line) solutions after incubation with increasing concentrations of Gd(NO3)3. Both AuNP solutions were used at the same concentration of 0.14 mM gold ions. (B) Evolution of UV-visible spectra of AuNP@BSPP in the presence of increasing concentrations of Gd(NO3)3 at t = 15 min. (C) Temporal evolution of UV-visible spectra of AuNP@BSPP for a concentration of Gd3+ ions equal to 10 μM. Spectra of AuNP@citrate are given in ESI, Fig. S8.† |
Therefore, AuNP@BSPP have a sensing limit for Gd3+ ions significantly lower than AuNP@citrate. Besides, it questions the mechanism of interaction of Gd3+ ions with the surface of AuNPs leading to the aggregation of AuNP@BSPP.
In order to obtain further information on the mechanism behind the observed changes, the study of the evolution of the absorbance spectra was carried out at different concentrations of Gd(NO3)3. In agreement with the visual observation, the wavelength corresponding to the maximum of the peak is progressively red-shifted from 523 nm up to 636 nm for concentration of Gd(NO3)3 increasing from 0 to 60 μM (Fig. 3B and ESI Fig. S7†). Additionally, the recording of the temporal evolution of the absorbance spectra every 15 minutes during 4 hours shows an evolution of the global aspect of the spectra (Fig. 3C). In contrast to AuNP@BSPP, whatever the concentration of Gd(NO3)3 and regardless of the measurement time, no evolution is observed in the case of AuNP@citrate solutions (see ESI Fig. S8†). In order to analyze quantitively these results, we further used the semiempirical spectroscopic flocculation parameter (FP) as described by Mayya et al.15 FP was calculated from normalized spectra by calculating the integration between 600 and 800 nm from which the integrated absorption for pristine AuNP@BSPP between the same limits was subtracted (for more details see ESI Fig. S9†). Fig. 4A illustrates the time dependence of the flocculation parameter of AuNP@BSPP at different concentrations in Gd(NO3)3. AuNP@BSPP aggregation increases with time to reach a plateau and at increasing rates with the Gd(NO3)3 concentration. The experimental kinetic data were analyzed by fitting the flocculation parameter by using a mono-exponential eqn (1)
FP = FPmax(1 − exp(−t/τF)) | (1) |
Fig. 4 (A) Time dependence of the FP of AuNP@BSPP plotted for increasing concentrations in Gd(NO3)3 together with the best fit to eqn (1). (B) Corresponding FP at 4 h (black dots) and aggregation rate (blue dots) plotted vs. concentrations of Gd(NO3)3. |
Fig. 4B illustrates the evolution of the flocculation parameter recorded at different concentrations for t = 4 h. First, a continuous increase is observed when the concentration of Gd(NO3)3 is varied from 2 to 18 μM. These results evidence the high detection capacity of AuNP@BSPP for considerably low Gd(NO3)3 concentrations and could be easily exploited to develop a colorimetric test. The validation of this approach to determine gadolinium content was carried out following the recommendations of standard ISO 5725 and 17025. For the chosen concentration of NPs, the method presents a linear range: 0 to 18 μM (FP = 7.118 × [Gd] − 6.994; R2 = 0.974). The detection limits are [Gd]LD = 0.74 μM and FPLD = 5.27 nm and the quantification limits are [Gd]LQ = 4.76 μM and FPLQ = 33.90 nm. The repeatability of the method was estimated from a series of nine independent measurements. From this, the coefficient of variation of repeatability, i.e. the ratio of the standard deviation to the mean, was calculated and is equal to 8.8%. This gives a measure of the dispersion of data points around the mean (see details of the calculation in the ESI†). This calibration line will be used in the last part of this article.
Moreover, in order to follow the effect of the concentration of Gd(NO3)3 on the relative rate of AuNP@BSPP aggregation, the maximum slope (Fmax/τF) of the flocculation curves was also plotted vs. Gd(NO3)3 concentration17 (Fig. 4B). At low concentrations, the aggregation rate is small and increases progressively when the concentration is varied from 6 to 28 μM. Beyond this concentration, the aggregation rate reaches a plateau and becomes constant. The observed aggregation of AuNP@BSPP may reflect the well-known process of coagulation induced by the addition of electrolytes. This process, described by the DLVO theory, predicts, as observed here, a slow and fast aggregation regime. The threshold salt concentration needed to induce rapid aggregation (here 28 μM) is referred to as the critical coagulation concentration (CCC).18 The Schulze–Hardy rule demonstrates a relationship between CCC of colloids and the valence of extra counter ionic electrolytes (z).19 Accordingly, divalent and trivalent ions are much more capable of causing precipitation of colloids from their suspensions than the monovalent ones.
The influence of the valence of cations on the relative aggregation rate was further studied in order to gain more insights into the aggregation process of AuNP@BSPP, in comparison to that of AuNP@citrate. In addition to Gd3+ ions, we studied the influence of Ca2+ divalent and Na+ monovalent ions. The effect of the concentration of these different cations on the relative aggregation rate is depicted in Fig. 5 and ESI Fig. S10.†
Fig. 5 Comparison of aggregation behavior of AuNP@BSPP (black plot) with that of AuNP@citrate (red plots) in the presence of mono, di and trivalent cations (NaCl, Ca(NO3)2 and Gd(NO3)3) respectively. |
For the three ions and for both types of NPs, the characteristic slow and fast aggregation regimes are evidenced. Moreover, the values of CCCs lie between 10 and 100 mM for Na+ ions, around 1 mM for Ca2+ ions and between 0.01 and 0.1 mM for Gd3+ ions. The CCCs which separate the two regimes decrease in order of monovalent, divalent and trivalent ions which is in agreement with the Schulze–Hardy rule.18 For the monovalent Na+ ions the CCC for AuNP@BSPP is higher than the value for AuNP@citrate: 100 mM and 50 mM respectively. This difference reflects the higher negative charge (zeta potential −40 ± 5 mV) and the higher stability of AuNP@BSPP compared with the AuNP@citrate (zeta potential −35 ± 3 mV). This is in agreement with an aggregation mainly induced by the compression of the electrical double layer of the NPs. For the divalent ions the same CCCs are observed for the two kinds of NPs, indicating a stronger adsorption of divalent ions to the surface than the monovalent ones.18 Noteworthily, this tendency is reversed for Gd3+ ions. The CCC of AuNP@BSPP of 0.03 mM is one order of magnitude lower than for the AuNP@citrate (0.3 mM). This reversed trend could be attributed to a specific and more effective interaction of the Gd3+ ions with the negative sulfo-groups stabilizing the AuNP@BSPP than with the citrate groups stabilizing the AuNP@citrate.20
The interaction of citrate and BSPP with bare gold surfaces was studied first. Solutions of citrate (24 mM in water, pH 5.5) and BSPP (24 mM in water, pH = 6.5) were deposited at a flow rate of 40 μL min−1. A decrease in frequency was observed suggesting the attachment of both molecules on the gold surface (ESI Fig. S11.1†). A surface coverage of 0.3 molecules per nm2 was calculated using the Sauerbrey equation for both citrate and BSPP. However, during the rinsing step almost all the adsorbed citrate was washed out, causing the frequency to increase progressively until almost reaching its initial value. This is consistent with a weak interaction of citrate with the gold surface via Au–COO− electrostatic interactions estimated to be 2 kcal mol−1.32,33 In contrast, after the washing step, half of the BSPP molecules remain on the gold surface leading to an apparent surface coverage of retained phosphine equal to Γ = 0.14 molecules per nm2. This difference with citrate is expected according to the stronger Au–P interaction which is about 15–20 kcal mol−1.34 Additionally, BSPP bearing two Ph–SO3− functions (pKa of −2.8), suggests cooperative or competitive participation of Au–SO3− electrostatic interactions during the adsorption process. This could induce steric hindrances on the surface that could be responsible for low adsorption behavior and partial desorption of BSPP as reported for QCM-D studies.35,36
In view of these results, the preparation of gold substrates for the subsequent Gd3+ ion deposition consisted first in their overnight incubation with citrate and BSPP solutions (24 mM in water). Concerning the further adsorption of Gd3+ ions, in order to avoid desorption of citrate ions, injection of Gd3+ ions was performed by keeping constant the concentration of citrate (24 mM) throughout the experiment.23 In the case of BSPP, the substrate was rinsed, equilibrated before the adsorption of Gd3+ ions and eluted with water. Fig. 6A and ESI Fig. S11.2† show the evolution of ΔF as a function of time when the measurements were carried out as sequential depositions of solutions of Gd(NO3)3 of increasing concentrations. The resulting surface coverage, calculated with the Sauerbrey equation, as a function of Gd3+ concentration is depicted in Fig. 6B. These curves were subsequently fitted using Langmuir and Langmuir–Freundlich isotherm models describing the interaction of the adsorbing molecule, i.e. the Gd3+ ion, with the adsorption surface sites (see ESI Fig. S11.3† for details).37,38
For the adsorption onto the BSPP coated substrate the experimental data were best fitted by the Langmuir isotherm model (R2 = 0.93) that assumes gradual saturation of sorption sites, without lateral interactions between adsorbed molecules, producing monolayer adsorption on a homogeneous adsorbent surface. This suggests a strong specific interaction of Gd3+ ions with the phosphine coated substrate. Rinsing with pure water increases the frequency to the level registered for the phosphine-coated substrate (see Fig. 6A) thus confirming that the phosphine was not washed out during the experiment. Additionally, the results of the experiments conducted on the adsorption of Gd3+ on a bare gold substrate (see ESI Fig. S11.4†) show differences, excluding then a potential displacement of the phosphine passivating layer during the Gd3+ adsorption. In the case of the interaction of Gd3+ ions with a citrate coated substrate, the adsorption of the Gd3+ ions onto the citrate coated substrate did not obey a Langmuir type isotherm model. The fitting parameter n = 2.4 of the Langmuir–Freundlich isotherm (R2 of 0.998, see Table S11.3†) may be identified as describing a cooperative interaction.39 This probably accounts for a mechanism of adsorption via the complexation between the Gd3+ ions and the carboxylic groups of the citrate ligand.40
This result stresses that the adsorption mechanisms onto the two surfaces are significantly different and confirms the observations on the NPs. Different adsorption scenarios on the two different surfaces are also confirmed by the plot of the measured energy dissipation per unit of mass (ΔD) vs. frequency (ΔF)41,42 (Fig. 7).
Fig. 7 ΔD versus ΔF plot for the Gd3+ ions adsorbed onto the citrate (red dots) and onto the BSPP coated gold surfaces (black dots), respectively. |
Concerning the BSPP coated surface, the ΔD/ΔF ratio remains constant suggesting an interaction of Gd3+ ions as a single layer via specific interactions.42 On the contrary, for citrate coated surfaces, the nonlinear variation of the ΔD with the ΔF can be related to the formation of loosely bound conformations between citrate or/and its complexes with the Gd3+ ions and the gold substrate.42 These weak interactions with the gold substrate induce a full desorption of citrate and Gd3+ ions after rinsing the surface with pure water (see Fig. 6A and ESI Fig. S11.5†). As a consequence of the specific interaction between Gd3+ ions and the phosphine coated substrate, measurements as sequential depositions of increasing Gd3+ concentrations with a washing step in between each deposition step show full reversibility, and short responses and recovery times (Fig. 8). Furthermore, the frequency response versus Gd3+ ion concentration shows a satisfactory linear behavior in-between the experimental concentration range (Fig. 8 inset).This QCM-D experiment accounts for the sensing performance of the Gd3+–Au–BSPP 2D-system and demonstrates the relevance to address an easier method to implement a bench test, based on the Gd3+–AuNP@BSPP 3D system.
Transmission Electron Microscopy (TEM) images realized of AuNP@BSPP after the addition of two different concentrations of Gd(NO3)3: 6 μM (for the slow aggregation regime) and 60 μM (for the fast one) are shown in Fig. 9 and ESI Fig. S12.† The aggregation of the NPs observed on the TEM images cannot be unambiguously interpreted due to drying-artifacts coming from the TEM sample preparation. However, a grey shell connecting the NPs is observed on both samples. This shell connects the NPs and is also found in their immediate surroundings. As investigated by Schubert et al.,43 this shell can be attributed to the presence of Gd hydroxides and can be considered to be an argument for the aggregation of the nanoparticles via interactions of sulfonate groups with the Gd3+ ions without replacement of the ligands from the first coordination sphere of Gd. Together, reversibility of the interactions observed in QCM-D experiments and the possibility to reverse the particle aggregation by the addition of a strong coordinating ligand for the Gd3+ ions, i.e. ethylenediamine tetra(methylene phosphonic acid) (EDTMP) (see ESI Fig. S13†) account for the labile character of the Gd3+ sulfonate interactions.
Fig. 9 TEM images of AuNP@citrate (left) and AuNP@BSPP (right) before and after incubation with 6 and 60 μM of Gd(NO3)3, respectively. |
Regarding the AuNP@citrate system, no change in the value of ζ-potential and in pH (i.e. 5.7), and thus, on the colloidal stability was evidenced after the addition of 25 μM of Gd3+ ions. Besides, no grey shell was detected on the TEM image (Fig. 9). The free carboxylic groups of the citrate ligand can now directly bind to the Gd3+ ions in the first coordination sphere of the ion by replacing water and/or hydroxy groups.40 From the literature results, this complex can be mainly described as a 1:1 complex between Gd3+ and citrate molecules.40 Hence, as the concentration of Gd3+ ions used in the experiments depicted in Fig. 3 is low compared to the concentration of citrate present in solution (about 10 times lower), the formation of 1:1 complexes with either the citrate in interaction with the surface of AuNPs or with the citrate free in solution is favored.48 Au surfaces retain their negative net charge as shown by ζ-potential measurements. This further prevents the aggregation process of AuNP@citrate solution in the presence of Gd3+ ions and makes the system unsuitable for the implementation of a colorimetric sensing test. On the contrary, the interaction between the sulfonate groups and the Gd3+ ions makes the AuNP@BSPP system extremely sensitive and suitable for the development of a cost-effective, fast and easy bench colorimetric assay (see Fig. 10).
Fig. 10 Schematic representation of the interaction of Gd3+ ions with the surfaces of AuNP@BSPP and AuNP@citrate, respectively. |
A colorimetric test using AuNP@BSPP was first applied as shown in Fig. 11B. As expected for the lower ratio 0.9, no color change was observed, whereas a ratio higher than 1.1 led to a change of observed color suggesting the presence of free Gd3+ ions.
Beyond this qualitative evaluation, quantitative measurements based on UV-visible spectroscopy (ESI Fig. S15†) and on the calibration curve presented in Fig. 3B were further performed. For this, the five solutions of HPICs were filtrated to separate free Gd3+ ions from obtained HPICs. Filtrates were then taken up to be used as samples for the colorimetric test. The first two filtrates, at ratios 0.9 and 1.1 do not contain any quantifiable amount of Gd3+. For the charge ratio 1.5, an estimation of Gd3+ free ion content of 13.2 ± 0.8 μM is measured, in good agreement with the 12 μM expected value.
Evaluation of the Gd3+ ions content for the two highest charge ratios is not relevant as the obtained values are not in the linear range determined previously. The determination of free Gd3+ ions through the use of the FP was found to be more precise than the one obtained by calculating the ratio of absorbance measured at two different wavelengths at 524 and 640 nm, respectively as proposed in the literature (see ESI Fig. S16† for comparison).3,51 The estimated value compares very favorably with the one estimated from ICP measurements 9.8 ± 0.5 μM with a higher accuracy. Hence, the application of the colorimetric test and the aggregation index method has proved to provide a good estimation of the concentrations of free gadolinium ions. The limits and ranges of detection of AuNP@BSPP are comparable with the ones obtained by conventional methods like chromatographic techniques coupled either with spectroscopic or with ICP techniques (see Table 1). Despite their simplicity, high sensitivity and convenience, few are the colorimetric tests based on AuNPs designed for the detection of lanthanide ions,3 thus justifying the importance to develop a colorimetric test based on AuNP@BSPP.
Analysis techniques | Gadolinium specie | Linear or fitting range of concentrations | Limits of detection | Limits of quantification | Ref. |
---|---|---|---|---|---|
a MEKC (Micellar Electrokinetic Capillary Chromatography). b N.P. = Not Precised. c HPLC (High Performance Liquid Chromatography). d ICP-AES (Inductively Coupled Plasma Atomic Emission Spectroscopy). e ESI-MS (Electrospray Ionization-Mass Spectrometry). f ICP-OES (Inductively Coupled Plasma Optical Emission Spectroscopy). | |||||
UV-vis | Gd3+ | 0–18 μM | 0.74 μM | 4.76 μM | This paper |
MEKCa/UV-vis | Gd-based contrasting agents | 5–200 μM or 100–5000 μM according to Gd CAs | 0.40–20 μM | N.P.b | 52 |
HPLCc/UV-vis | GdDTPA-BMA | 2–800 μM (serum), 10–2000 μM (urine) | 0.3 μM (serum), 1.1 μM (urine) | 2 μM (serum), 10 μM (urine) | 53 |
HPLCc/ICP-AESd | Gadodiamide | 0–590 μM (ICP-AES of serum) | 1.9 μM (ICP-AES of serum) | 6.5 μM (ICP-AES of serum) | 54 |
ESI-MSe/ICP-OEf | Gd-based contrasting agents | 5–100 μM | 0.1–1 μM | 0.5–5 μM | 55 |
HPLCc/ICP-OESf | Gd-based contrasting agents | 2.5–500 μM | 0.05–0.2 μM | 0.16–0.73 μM | 56 |
In a QCM-D experiment, the adsorption of molecules on the gold surface is assessed by monitoring the frequency shift (ΔF) and dissipation shift (ΔD) (the frictional and viscoelastic energy losses in the system) as a function of time. The changes in frequency are proportional to the changes in the wet-mass deposited on the gold surface according to the Sauerbrey equation57 (eq (2)):
(2) |
Footnote |
† Electronic supplementary information (ESI) available: Complementary results and techniques. See DOI: 10.1039/d0na00374c |
This journal is © The Royal Society of Chemistry 2020 |