Chiara
Abate
a,
Anna
Piperno
a,
Alex
Fragoso
b,
Ottavia
Giuffrè
a,
Antonino
Mazzaglia
c,
Angela
Scala
a and
Claudia
Foti
*a
aDipartimento di Scienze Chimiche, Biologiche, Farmaceutiche ed Ambientali, Università di Messina, Viale Ferdinando Stagno d'Alcontres 31, 98166 Messina, Italy. E-mail: cfoti@unime.it
bNanobiotechnology & Bioanalysis Group, Departament d'Enginyeria Química, Universitat Rovira i Virgili, Avinguda Països Catalans 26, 43007, Tarragona, Spain
cConsiglio Nazionale delle Ricerche, Istituto per lo Studio dei Materiali Nanostrutturati (CNR-ISMN), URT di Messina c/o Dipartimento di Scienze Chimiche, Biologiche, Farmaceutiche ed Ambientali, Università di Messina, Viale Ferdinando Stagno d'Alcontres 31, 98166 Messina, Italy
First published on 13th February 2023
A potentiometric study on the interactions of L-carnosine (CAR) (2-[(3-aminopropanoyl)amino]-3-(1H-imidazol-5-yl)propanoic acid) with two toxic metal cations, Hg2+ and Cd2+, is reported here. The elucidation of the metal (M2+)–CAR interactions in aqueous solution highlighted the speciation model for each system, the dependence of the formation constants of the complex species on ionic strength (0.15 ≤ I/mol L−1 ≤ 1) and temperature (288.15 ≤ T/K ≤ 310.15) and changes in enthalpy and entropy. The sequestering ability of CAR towards the two metal ions was quantified and compared with that with Pb2+, previously determined. Considering the complexing ability of CAR and its unclear electrochemical properties, a more electroactive derivative, the ferrocenyl-carnosine (FcCAR), was synthesized and its complexing ability was evaluated by UV-vis spectroscopy. FcCAR electrochemical properties were investigated by Cyclic Voltammetry (CV) and Differential Pulse Voltammetry (DPV) on Screen-Printed Electrodes (SPEs), to evaluate its sensing properties. Electrochemical responses in the presence of Hg2+ and Pb2+ have been shown to be promising for the electrochemical detection of these metal cations in aqueous environment.
![]() | ||
Fig. 1 Chemical structures of L-carnosine (CAR) and the newly synthesized ferrocenyl-carnosine (FcCAR). |
Although the specific biological role of CAR is not completely understood, many studies highlighted its extensive antioxidant potential as an effective quencher of intracellular reactive oxygen species (ROS) and reactive nitrogen species (RNS), as well as a scavenger of reactive carbonyl species (RCS).3–10 The physiological behavior of CAR depends on its complexation of bivalent metal cations, e.g., Cu2+, Mn2+, Zn2+, Ru2+, Co2+, Ni2+, Cd2+, Mg2+, and Ca2+.1 It is a polydentate ligand with five potential metal-coordinating sites, i.e., two imidazole nitrogens, the carboxylate group, a peptide linkage and a terminal amino group. CAR can form both tetrahedral and octahedral types of complexes, but their exact configuration depends on the size of the metal cation, ligand-to-metal ratios, and ionic strength of the supporting electrolyte.1 In this regard, the thermodynamic behavior of Ca2+, Mg2+, Cu2+, Mn2+, Zn2+, and Pb2+-CAR systems was recently elucidated.2,5,11 Therefore, the present study focused on the determination of the thermodynamic interaction parameters of CAR with Hg2+ and Cd2+ by means of potentiometry in NaCl aqueous solutions with different ionic strengths (0.15 ≤ I/mol L−1 ≤ 0.96) and temperatures (288.15 ≤ T/K ≤ 310.15).
Considering the advantageous complexing ability of CAR and its poorly detailed electrochemical properties,1,12–14 we synthesized the ferrocenyl-carnosine (FcCAR, Fig. 1) as an electroactive CAR derivative for metal cation sensing applications. The conjugation of aminoacids and proteins with ferrocene units is well exploited in the literature leading to redox-active materials with interesting electron-transfer properties.15–17 The functionalization of the amine group of the β-alanine residue did not affect the multiple recognition sites of CAR (i.e., imidazole ring and amino and carboxylic groups) and meanwhile strengthened the electrochemical applications of CAR by the redox-active ferrocene unit.18–21 FcCAR was synthesized by a coupling reaction between N-hydroxysuccinimide activated ferrocene and CAR in the presence of sodium bicarbonate and it was characterized by analytical and spectroscopic techniques. To the best of our knowledge, no reports of ferrocene–carnosine conjugates, which may offer the potential for the development of metal specific probes, have been described in the literature. In this paper, we provide a full account of the complexing ability of CAR together with the spectroscopic and electrochemical properties of the first ferrocene–carnosine conjugate (FcCAR) with the aim to evaluate its sensing properties.
Potentiometric titrations were performed by adding NaOH standard to 25 mL of CAR solutions (1 ≤ CL/mmol L−1 ≤ 6), containing Hg2+ or Cd2+ (0.5 ≤ CM/mmol L−1 ≤ 3), HCl (5 ≤ CH/mmol L−1 ≤ 12) and NaCl (0.15 ≤ CNaCl/mol L−1 ≤ 0.96). Measurements were carried out at constant temperature (288.15 ≤ T/K ≤ 310.15) using thermostated glass jacket cells, under constant magnetic stirring and nitrogen bubbling in order to ensure homogeneity of the systems and avoid possible interferences of air O2 and CO2 inside. To determine the standard electrode potential, E°, and pKw values, independent titrations of HCl with standard NaOH solutions were carried out for each measurement under the same experimental conditions of ionic strength and temperature. The potentiometric data were elaborated using BSTAC4 and STACO4 computer programs.22 Both determined the purity of the reagents, formal potential, E°, the liquid junction potential coefficient ja, Ej = ja[H+] and formation constants of the species. Speciation diagrams were obtained by means of the HySS program.23
As the potentiometric measurements, the spectrophotometric measurements were carried out as titrations in a wide selected wavelength range (200 ≤ λ ≤ 400 nm). For acid–base studies, 25 mL of solutions containing FcCAR (0.04 ≤ CL/mmol L−1 ≤ 0.15), HCl (3 mmol L−1), and NaCl (I = 0.15 mol L−1) were titrated with standard NaOH in the pH range 3–9.5. For metal complex studies, 25 mL of the solutions containing FcCAR (0.02 ≤ CL/mmol L−1 ≤ 0.04), Hg2+ or Pb2+ (0.01 ≤ CM/mmol L−1 ≤ 0.02, varying the metal:
ligand ratio 0.5 ≤ CM/CL ≤ 2), HCl (0.2 mmol L−1) and NaCl (I = 0.15 mol L−1) were titrated with standard NaOH in the 3 ≤ pH ≤ 9.5 pH range.
The spectrophotometric data were elaborated using the HYSPEC computer program24 able to analyze the UV-vis spectra, determining the formation constants of the species, as well as the molar absorption coefficients.
The redox properties of FcCAR were assessed by Cyclic Voltammetry (CV) and Differential Pulse Voltammetry (DPV) in the potential range −1 to +1 V (vs. Ag/AgCl) in 0.1 mol L−1 KCl. Metal solutions were prepared in MOPS buffer (pH = 7). CV was performed at 0.1 V s−1. DPV parameters were set as follows: increment potential of each pulse = 0.01 V, amplitude = 0.1 V, pulse width = 0.05, sample width = 0.0025 s and pulse period = 0.1 s.
The ferrocenyl intermediate (2) (821 mg; 2.50 mmol) was dissolved in DMF (25 mL) and slowly added, under stirring, in an ice bath, to a CAR (678.9 mg; 3.0 mmol), NaHCO3 (210.3 mg; 2.50 mmol) and H2O/DMF (1:
1) solution. The reaction mixture was stirred at room temperature for 20 h. The solvent was evaporated under vacuum and the brown solid was purified by crystallization from water/acetone to obtain FcCAR (3) in 64% overall yield.
1H NMR (D2O, 500 MHz): δ 7.66 (s, 1H), 6.85 (s, 1H), 4.27 (m, 2H), 4.20 (m, 2H), 4.04 (m, 1H), 3.96 (m, 5H), 3.13–2.93 (m, 2H), 2.90–2.78 (m, 2H), 2.37–2.26 (m, 2H). 13C NMR (D2O:
acetone-d6, 125 MHz): δ 179.22, 174.73, 173.01, 136.90, 134.28, 118.86, 71.53, 56.57, 56.34, 37.30, 37.23, 33.56. ESI-MS (m/z): 439.10 detected as [MH]+ species cld for C20H22FeN4O4 (m/z: 438.099).
The most reliable speciation models for both systems were chosen on the basis of general criteria, such as simplicity, standard and mean deviation of the fit, as well as formation percentage of species.29,30 The experimental formation constant values of the Hg2+- and Cd2+-CAR species, under different conditions of temperature and ionic strength, are listed in Table 1 and expressed as global formation constants, β, which refers to the following reaction:
M2+ + iH+ + L− = MHiL2+i−1 | (1) |
log![]() |
|||||||
---|---|---|---|---|---|---|---|
M | Species | I = 0.15b | I = 0.49b | I = 0.72b | I = 0.96b | I = 0.15b | I = 0.15b |
T = 298.15 K | T = 288.15 K | T = 310.15 K | |||||
a Refers to reaction (1). b Expressed in mol L−1. c ≥95% of confidence interval. | |||||||
Hg2+ | ML+ | 17.28 ± 0.01c | 17.61 ± 0.02c | 18.08 ± 0.03c | 18.36 ± 0.01c | 17.49 ± 0.08c | 16.81 ± 0.02c |
MLH2+ | 24.37 ± 0.02 | 25.20 ± 0.04 | 26.03 ± 0.07 | 25.60 ± 0.07 | 25.26 ± 0.02 | 23.63 ± 0.07 | |
MLOH0 | 9.46 ± 0.03 | 8.90 ± 0.02 | 9.03 ± 0.02 | 9.07 ± 0.02 | 10.38 ± 0.04 | 8.95 ± 0.02 | |
Cd2+ | ML+ | 3.11 ± 0.07 | 3.68 ± 0.05 | 3.90 ± 0.05 | 4.13 ± 0.06 | 4.22 ± 0.04 | 3.42 ± 0.08 |
MLH2+ | 12.17 ± 0.03 | 12.69 ± 0.03 | 12.96 ± 0.06 | 13.15 ± 0.03 | 13.07 ± 0.03 | 11.80 ± 0.08 | |
MLH23+ | 18.85 ± 0.03 | — | — | — | — | — |
Formation of three complex species, namely HgL+, HgLH2+, and HgLOH0 for the Hg2+-CAR system and CdL+, CdLH2+ and CdLH23+ for Cd2+-CAR was found. The stability of ML and MLH species increases as the ionic strength grows and, vice versa, it decreases from T = 288.15 K to T = 310.15 K. The HgLOH0 species shows a different behavior, as well as CdLH23+, whose quantity was only relevant at I = 0.15 mol L−1 and T = 298.15 K, and negligible under the other conditions.
The speciation profile relating to the Hg2+-CAR system (Fig. 2a) better highlights the formation of the metal complex species throughout the pH, proving the binding ability of CAR towards the metal cations at I = 0.15 mol L−1 and T = 298.15 K. The high stability constants of Hg2+-CAR allowed the suppression of the hydrolysis of the metal cation. Instead, the Hg2+-Cl− species prevailed up to pH ≅ 5. The HgL+ species formed starting from pH ≅ 5.5, reaching a 0.47 mole fraction at pH ≅ 7.5 in NaCl aqueous solution (CM = 2 mmol L−1 and CL = 4 mmol L−1). A minor fraction of the HgLH2+ complex was found at 4 ≤ pH ≤ 9. The HgLOH0 species was present starting from pH ≅ 6.5 and totally prevailed at pH = 9. The distribution concerning the Cd2+-CAR system (Fig. 2b) was noticeably different, due to the lower formation percentage of the species, which was always below 0.2. An amount of free cadmium (0.1 metal fraction) was always present, as well as the Cd2+-Cl− species.
The formation constants of Table 1 were used to study the dependence on ionic strength and temperature following the Debye–Hückel type (2) and van't Hoff (3) equations, respectively:31–33
![]() | (2) |
log![]() ![]() ![]() ![]() | (3) |
In eqn (2), β and β0 correspond to the stability constants at a given ionic strength and infinite dilution respectively, z* = ∑(charge)2reactants − ∑(charge)2products, and C is an empirical parameter. In eqn (3), logβT is the stability constant at a given temperature T (expressed in Kelvin) and ionic strength, log
βθ is the value at the reference temperature θ (T = 298.15 K) and R = 8.314472 J K−1 mol−1 when ΔH is expressed in kJ mol−1. The calculated values of log
β0 and C, for the dependence on ionic strength, and ΔH, for the dependence on temperature, are reported in Table 2. In the same table, calculated ΔG (ΔG = −RT
ln
β) and TΔS (TΔS = ΔH − ΔG) values are also reported to have a complete thermodynamic picture. All the enthalpy change values (ΔH) concerning the formation of Hg2+ and Cd2+-CAR species involved exothermic processes, along with negative entropy change values (TΔS). Among them, the ML species for the Hg2+-CAR system was the only one with a positive TΔS, suggesting a rise of the order due to the solvation processes. The thermodynamic parameters reported in Table 2 are very useful for predictive purposes allowing the calculation of the formation constants at any value of ionic strength and temperature in the range 0 ≤ I/mol L−1 ≤ 1 and 278.15 ≤ T/K ≤ 318.15. In Table 2, thermodynamic parameters concerning the formation of the Pb2+-CAR system, previously determined, are also reported,11 useful for later considerations.
M | Species | log![]() ![]() |
C | ΔGa,b,c | ΔHa,b,c | TΔSa,b,c |
---|---|---|---|---|---|---|
a Refers to reaction (1).
b In kJ mol−1.
c At I = 0.15 mol L−1 (NaCl).
d ≥95% of confidence interval.
e ![]() |
||||||
Hg2+ | ML | 17.54 ± 0.01d | 1.8 ± 0.1d | −98.6 | −65 ± 10d | 34 |
MLH | 24.42 ± 0.02 | 2.1 ± 0.2 | −139.1 | −162 ± 14 | −23 | |
MLOH | 9.75 ± 0.01 | 0.1 ± 0.1 | −54.0 | −118 ± 11 | −64 | |
Cd2+ | ML | 3.44 ± 0.12 | 1.6 ± 0.2 | −17.8 | −60 ± 40 | −42 |
MLH | 12.26 ± 0.11 | 1.4 ± 0.2 | −69.5 | −98 ± 30 | −29 | |
Pb2+![]() |
ML2 | 9.93 | −0.24 | −56.7 | −122 | −65 |
ML2H | 18.91 | −0.24 | −107.9 | −87 | 21 |
On the basis of the thermodynamic interaction parameters, the sequestering ability of CAR towards the two metal cations can be quantitatively assessed by the calculation of pL0.5. The latter is an empirical parameter that allows the quantification of the ability of a ligand to sequester a metal cation under specific conditions of temperature, ionic strength and pH. The pL0.5 corresponds to the cologarithm of the needed ligand concentration to bind 50% of the metal cation in traces, and it is determined by the following sigmoidal Boltzmann type equation with asymptotes equal to 1 for pL → −∞ and 0 for pL → +∞:31,34
![]() | (4) |
An example of the sequestering diagram under conditions simulating seawater (i.e., I = 0.7 mol L−1 and pH = 8.1, at T = 273.15 K) is reported in Fig. 3. In the diagram, along with Hg2+ and Cd2+, Pb2+ is also reported, whose interactions with CAR were recently studied11 and are provided in Table 2. As can be observed, the highest sequestering ability of CAR is towards Hg2+, following the trend:
Hg2+ ≫ Pb2+ > Cd2+ |
![]() | ||
Fig. 3 Sequestration diagram of CAR towards Hg2+, Pb2+ and Cd2+ ions at pH = 8.1, I = 0.7 mol L−1 and T = 273.15 K. |
With this in mind, we synthesized an electroactive CAR derivative (FcCAR) with the aim to evaluate its use as a sensor for Pb2+ and Hg2+. We did not consider Cd2+ cation since it is less involved in the coordination with CAR molecule.
![]() | ||
Fig. 4 Speciation diagram vs. pH of FcCAR (L) species (charges omitted for simplicity) in NaCl aqueous solution at I = 0.15 mol L−1 and T = 298.15 K (CL = 0.1 mmol L−1). |
Once the FcCAR acid–base behavior was defined, UV-Vis titrations were performed in the presence of metal cations in order to evaluate the strength of the interactions with Hg2+ and Pb2+. In particular, in the presence of Hg2+, the UV-vis spectra of the molecule were affected by a significant variation as reported in Fig. 5, where ε vs. λ values of the Hg2+ and Pb2+-L species are shown. This could be probably due to the involvement of the imidazole ring in the complexation. Indeed, the most trustworthy speciation model for the Hg2+-FcCAR system is reported in Table 4 and provides the formation of three complex species, namely ML, MLH and MLOH. The behavior of the Pb2+-FcCAR system is different, and the formation of two ML2 and ML2H complex species (Table 4) was achieved without, therefore, the involvement of the imidazole ring. In this case, we observed only the increase in absorbance, but the spectrum shape remained unchanged. For both systems, the speciation diagrams in Fig. 6 describe a strong chelating ability of FcCAR towards two metal cations. In particular, the Hg2+ fraction reached a maximum of 0.9 in the formation of the MLH and ML species at 3 ≤ pH ≤ 5 and 7 ≤ pH ≤ 8, respectively. The MLOH species formed starting from pH ≥ 7. On the other hand, Pb2+ was totally coordinated by FcCAR as PbL2H or PbL2.
![]() | ||
Fig. 5 ε vs. λ of the (a) Hg2+- and (b) Pb2+-FcCAR (L) species (charges omitted for simplicity) in NaCl aqueous solution at I = 0.15 mol L−1 and T = 298.15 K. |
The high complexing capacities of FcCAR were also reflected in the sequestering abilities, calculated using eqn (4). The comparison of the sequestering ability of CAR and FcCAR with respect to Pb2+ and Hg2+ is shown in Fig. S3 of the ESI.† For both systems, an increase in the pL0.5 value of at least three orders of magnitude was obtained.
The redox properties of FcCAR were investigated by means of CV at different potential windows (−1.0 ≤ E(V) vs. Ag/AgCl ≤ +1.0), pH (3 ≤ pH ≤ 9 at scan rate: 0.1 V s−1) and scan rate ranges (10 ≤ mV s−1 ≤ 100 at pH = 7 (Fig. 7 and Fig. S4†). As can be observed in Fig. 7, there are small ΔEp variations as the pH changes in the CVs as a function of pH. While the cathodic peaks remain essentially unchanged, anodic peaks are anodically displaced by 20 mV from pH 3 to pH 9, indicating a slight hindrance in the oxidation of Fc due to deprotonation of the carnosine residue. Interestingly, the CV of FcCAR revealed the appearance of a small oxidation peak at ∼0.6 V and pH 7 that is displaced to lower potentials as the pH increases (0.526 V at pH = 9). This peak is due to the oxidation of the imidazole ring of carnosine, as reported in the literature,13 which is favored as deprotonation of the imidazole ring occurs.
![]() | ||
Fig. 7 CVs of FcCAR (1 mmol L−1) in 0.1 mol L−1 KCl aqueous solution at different pH values (3 ≤ pH ≤ 9) and room temperature (scan rate = 0.1 V s−1). |
To evaluate the FcCAR sensing activity, electrochemical titrations were performed by adding Hg2+ or Pb2+ (0.5 ≤ CM/mmol L−1 ≤ 3, in MOPS buffer at pH = 7) to FcCAR solutions. CV and DPV titrations were performed in a narrower potential range (−0.5 ≤ E(V) vs. Ag/AgCl ≤ +0.5), further restricted in Fig. 8 and 9 to focus only on the FcCAR signal. As can be observed, FcCAR peaks decrease in intensity as the metal concentration increases. The trend of cathodic peak currents vs. metal concentration is underlined in Fig. 10. The peak current linearly decreases in the ranges 0.5 ≤ CM/mmol L−1 ≤ 3.0 for Hg2+ and 0.5 ≤ CM/mmol L−1 ≤ 1.7 for Pb2+. This decrease may be due to the coordination of both heavy metals to the CAR moiety, which markedly increases the molecular weight of the complex and reduces its diffusion coefficient and, hence, the peak current. In the case of addition of Hg2+, the peak potentials are not changed up to a 1:
1 stoichiometry and are then cathodically shifted. This suggests that the coordination of this cation to FcCAR promotes its oxidation by stabilizing the electrogenerated ferrocenium cation in the anionic Hg-FcCAR complex or by being reduced to Hg+.35 In contrast, the Pb2+ complex is neutral and oxidation of Fc destabilizes the complex by electrostatic repulsion with the metal center, provoking an anodic shift of the peak potential even for substoichiometric M:L molar ratios.36 This voltametric behavior suggests that FcCAR could be used as a signal-off detection system for heavy metals.
![]() | ||
Fig. 8 CV titrations of FcCAR (1 mmol L−1) with Hg2+ in 0.1 mol L−1 KCl aqueous solution at pH = 7 and room temperature (scan rate = 0.1 V s−1). |
![]() | ||
Fig. 9 DPV titrations of FcCAR (1 mmol L−1) with (a) Hg2+ and (b) Pb2+ in 0.1 mol L−1 KCl aqueous solution at pH = 7 and room temperature. |
Footnote |
† Electronic supplementary information (ESI) available. See DOI: https://doi.org/10.1039/d2dt04093j |
This journal is © The Royal Society of Chemistry 2023 |