On the Development of Selective Chelators for Cadmium: Synthesis, Structure and Chelating Properties of 3-((5-(trifluoromethyl)-1,3,4-thiadiazol-2-yl)amino)benzo[d]isothiazole 1,1-dioxide, a Novel Thiadiazolyl Saccharinate

Aquatic contamination by heavy metals is a major concern for the serious negative consequences it has for plants, animals, and humans. Among the most toxic metals, Cd(II) stands out since selective and truly efficient methodologies for its removal are not known. We report a novel multidentate chelating agent comprising the heterocycles thiadiazole and benzisothiazole. 3-((5-(trifluoromethyl)-1,3,4-thiadiazol-2-yl)amino)benzo[d]isothiazole 1,1-dioxide (AL14) was synthesized from cheap saccharin and characterized by different techniques, including single crystal X-ray crystallography. Our studies revealed the efficiency and selectivity of AL14 for the chelation of dissolved Cd(II) (as compared to Cu(II) and Fe(II)). Different spectral changes were observed upon the addition of Cd(II) and Cu(II) during UV-Vis titrations, suggesting different complexation interactions with both metals.


Introduction
Contamination of aquatic systems with heavy metals is a long-standing problem that mostly affects rivers and estuaries where effluents are discharged or to where debris is leached. Several studies point to excessive amounts of metals in the aquatic systems worldwide [1,2], with harmful consequences for aquatic species (e.g., fishes, bivalves, crustaceans, algae [3,4]) and for human health [5,6] as a result of their bioaccumulation and propagation through the food chain.
In this context, the development of effective tools for the selective sequestration of toxic metals is a major challenge. Cadmium is among the toxic metals frequently detected in aquatic systems, mostly arising from the intense industrial, agricultural, and mining activity [7]. Previous studies [8][9][10][11][12][13][14][15][16] focused on adsorption and bioremediation yielded methods that enabled the sequestration of cadmium, but proved unspecific, as other metals were found to be preferentially adsorbed. Thus, the development of specific and effective tools for solving the problem of environmental contamination by cadmium remains a top priority. In recent years, we have designed tetrazole-saccharinates [17][18][19][20] and demonstrated their effective and selective chelation capabilities for Cu(II) [17]. It was also demonstrated that the ligands are non-toxic while their corresponding copper complexes proved highly cytotoxic toward several cancer cell lines, suggesting their application in chelant-based antineoplastic chemotherapy. Although useful as tools for selective sequestration of Cu(II), with possible impact in medicine and environmental remediation, tetrazole-saccharinates proved photolabile due to the photoreactivity of the tetrazole moiety [18,21,22]. Optimization of the saccharinate-based conjugates, involving replacement of the partner heterocycle, yielded thiadiazolyl-saccharinates with remarkable properties [19]. In this work, we disclose the synthesis, crystal structure, and chelating properties of 3-((5-(trifluoromethyl)-1,3,4-thiadiazol-2-yl)amino)benzo[d]isothiazole 1,1-dioxide (AL14; Scheme 1), a novel thiadiazolyl-saccharinate that proved to selectively chelate cadmium from aqueous solution.
The one-dimensional (1D) and two-dimensional (2D) NMR (Nuclear Magnetic Resonance) data (Supplementary Information, Figures S1-S6) proved the structure of AL14: the four protons of the benzisothiazole moiety can be undoubtedly confirmed by 1 H NMR (Supplementary Information, Figure S1), following verification by its TOCSY (Total Correlation Spectroscopy) correlations and HSQC (Heteronuclear Single Quantum Coherence) spectra ( Supplementary Information, Figures S3 and S4). Additionally, the HMBC (Heteronuclear Multiple Bond Correlation) spectra allowed one to thoroughly identify the carbons of saccharin moiety ( Supplementary Information, Figures S5 and S6), enabling better identification of the carbons adjacent to the trifluoromethyl group ( Figure 1, Table  1). It is noteworthy that the data reveal the presence of the thiadiazolyl saccharinate in its amino-linked tautomeric form, as also observed in the crystal phase.
The one-dimensional (1D) and two-dimensional (2D) NMR (Nuclear Magnetic Resonance) data (Supplementary Information, Figures S1-S6) proved the structure of AL14: the four protons of the benzisothiazole moiety can be undoubtedly confirmed by 1 H NMR (Supplementary Information, Figure S1), following verification by its TOCSY (Total Correlation Spectroscopy) correlations and HSQC (Heteronuclear Single Quantum Coherence) spectra ( Supplementary Information, Figures S3 and S4). Additionally, the HMBC (Heteronuclear Multiple Bond Correlation) spectra allowed one to thoroughly identify the carbons of saccharin moiety (Supplementary Information, Figures S5 and S6), enabling better identification of the carbons adjacent to the trifluoromethyl group ( Figure 1, Table 1). It is noteworthy that the data reveal the presence of the thiadiazolyl saccharinate in its amino-linked tautomeric form, as also observed in the crystal phase.

X-ray Crystal Analysis
A single-crystal X-ray crystallography study unambiguously showed that the tautomeric form present in the crystalline state is that depicted in the ORTEP shown in Figure 2 that also depicts the atom labelling scheme. Indeed, all H-atoms could clearly be located from the difference electron density maps. The compound crystallizes in the centrosymmetric triclinic space group P−1.

Metal Chelating Activities
Driven by the chelating properties evidenced by previously developed saccharinbased conjugates, the chelating activity of 3-((5-(trifluoromethyl)-1,3,4-thiadiazol-2yl)amino)benzo[d]isothiazole 1,1-dioxide (AL14) was first evaluated for Cd(II), Cu(II), and Fe(II), dissolved in water, at different concentrations (1, 5, 10 mM). The results presented in Table 2 reveal a considerably higher chelating activity of AL14 for Cd(II) than for Cu(II) and undetected activity for Fe(II). The results are very important, since most of the studies reporting methodologies to remove Cd(II) from aquatic system are non-selective or preferentially remove other metal ions over cadmium [8,10,[12][13][14][15][16]. The number of studies focusing on the specific sequestration of Cd(II) from water is very small [23,24] and a direct comparison with our results is difficult since different experimental conditions were used.  In the crystal, the five-and six-membered rings of the fused benzothiazole group are coplanar, the angle between the least-squares planes of the two rings being 0.57(3) • . The least squares planes of the five-membered thiadiazol-ring and the fused nine-membered ring are closely but not strictly coplanar, the dihedral angle being 7.10(3) • . The molecule has conformational flexibility around the C3-N12 and N12-C13 bonds, but the S14-C13-N12-C3 and C13-N12-C3-N2 torsion angles observed in the crystal are small, being −5.4(2) • and 3.7(2) • , respectively. Overall, the molecule skeleton is closer to planarity as compared to the sulfanyl-bridged thiadiazolyl-saccharinate reported in [19]. The CF 3 group is disordered over two alternate positions.

Metal Chelating Activities
Driven by the chelating properties evidenced by previously developed saccharinbased conjugates, the chelating activity of 3-((5-(trifluoromethyl)-1,3,4-thiadiazol-2yl)amino)benzo[d]isothiazole 1,1-dioxide (AL14) was first evaluated for Cd(II), Cu(II), and Fe(II), dissolved in water, at different concentrations (1, 5, 10 mM). The results presented in Table 2 reveal a considerably higher chelating activity of AL14 for Cd(II) than for Cu(II) and undetected activity for Fe(II). The results are very important, since most of the studies reporting methodologies to remove Cd(II) from aquatic system are non-selective or preferentially remove other metal ions over cadmium [8,10,[12][13][14][15][16]. The number of studies focusing on the specific sequestration of Cd(II) from water is very small [23,24] and a direct comparison with our results is difficult since different experimental conditions were used.

Metal Chelating Activities
Driven by the chelating properties evidenced by previously developed saccharinbased conjugates, the chelating activity of 3-((5-(trifluoromethyl)-1,3,4-thiadiazol-2-yl) amino)benzo[d]isothiazole 1,1-dioxide (AL14) was first evaluated for Cd(II), Cu(II), and Fe(II), dissolved in water, at different concentrations (1, 5, 10 mM). The results presented in Table 2 reveal a considerably higher chelating activity of AL14 for Cd(II) than for Cu(II) and undetected activity for Fe(II). The results are very important, since most of the studies reporting methodologies to remove Cd(II) from aquatic system are non-selective or preferentially remove other metal ions over cadmium [8,10,[12][13][14][15][16]. The number of studies focusing on the specific sequestration of Cd(II) from water is very small [23,24] and a direct comparison with our results is difficult since different experimental conditions were used. These results clearly show that the novel compound AL14 may be able to selectively chelate Cd(II), compared to Cu(II) and Fe(II). This evidence is reinforced by the fact that the ratio between the ligand and the available metal is lower for Cd(II) than for Cu(II) and Fe(II). A higher ratio of ligand to metal has been associated with greater efficiency of the ligand, as a result of the higher number of binding sites available [14].
Since the ligand revealed a greater chelating activity for Cd(II) compared to Cu(II) and Fe(II), additional experiments were developed, now considering higher concentrations (15 and 20 mM) of ligand (AL14). The results show an increase in chelating activity with increasing concentrations, but this increase appears to be slower than that observed in the first experiments at lower concentrations (1-10 mM), suggesting that the equilibrium is being reached (Figure 4). For this set of experiments, the highest chelating activity achieved was 69.0 ± 3.3% for [ligand] = 20 mM and [Cd] = 9 mM. and Fe(II), additional experiments were developed, now considering higher c tions (15 and 20 mM) of ligand (AL14). The results show an increase in chelatin with increasing concentrations, but this increase appears to be slower than that in the first experiments at lower concentrations (1-10 mM), suggesting that the rium is being reached (Figure 4). For this set of experiments, the highest chelatin achieved was 69.0 ± 3.3% for [ligand] = 20 mM and [Cd] = 9 mM. In order to enable future comparison with the chelating capacity of other com the IC50 value for this novel compound was determined. In this context, the IC sponds to the concentration of compound (ligand) capable of removing 50% of concentration in solution. The lower the concentration required to remove 50 metal, the greater the chelating capacity of the compound. For this new ligand, t 7.857 mM, with a confidence interval (95%) ranging between 7.585 and 8.139.

UV-vis Titrations
Aiming to evaluate the spectral changes upon metal addition, experiments w formed by adding 2 to 40 µ L of aqueous Cd(II) solution (2 mM) to the ligand sol µ M, from 1 mM stock solution), in a quartz cuvette. Similar experiments were co with Cu(II), for comparative purposes. The spectrum of AL14 ( Figure 5) reve main bands between 200 and 400 nm. The first and most intense band lies betw and 230 nm (at these conditions, its maximum is at ca. 215 nm, Ɛ ≈ 2.06 × 10 4 M −1 it is mainly attributed to saccharin, in keeping with the spectra of other sacchari tives also synthesized by our team (data not yet published), and data available erature [25,26]. The second and third main bands appear between 240 and 300 n 9.14 × 10 3 M −1 cm −1 , at ca. 270 nm), and between 300 and 380 nm (Ɛmax ≈ 1.26 × 10 4 at ca. 339 nm), respectively. In order to enable future comparison with the chelating capacity of other compounds, the IC 50 value for this novel compound was determined. In this context, the IC 50 corresponds to the concentration of compound (ligand) capable of removing 50% of the metal concentration in solution. The lower the concentration required to remove 50% of the metal, the greater the chelating capacity of the compound. For this new ligand, the IC 50 is 7.857 mM, with a confidence interval (95%) ranging between 7.585 and 8.139.

UV-vis Titrations
Aiming to evaluate the spectral changes upon metal addition, experiments were performed by adding 2 to 40 µL of aqueous Cd(II) solution (2 mM) to the ligand solution (50 µM, from 1 mM stock solution), in a quartz cuvette. Similar experiments were conducted with Cu(II), for comparative purposes. The spectrum of AL14 ( Figure 5) reveals three main bands between 200 and 400 nm. The first and most intense band lies between 200 and 230 nm (at these conditions, its maximum is at ca. 215 nm, ε ≈ 2.06 × 10 4 M −1 cm −1 ) and it is mainly attributed to saccharin, in keeping with the spectra of other saccharin derivatives also synthesized by our team (data not yet published), and data available in the literature [25,26]. The second and third main bands appear between 240 and 300 nm (ε max ≈ 9.14 × 10 3 M −1 cm −1 , at ca. 270 nm), and between 300 and 380 nm (ε max ≈ 1.26 × 10 4 M −1 cm −1 , at ca. 339 nm), respectively.
In general, the addition of increasing amounts of Cd(II) promotes an increase in band intensity between 313 and 370 nm, accompanied by a decrease in intensity for wavelengths between 250 and 313 nm, making it possible to identify an isosbestic point at 313 nm ( Figure 5). In turn, the addition of the same increasing amounts of Cu(II) causes an increase in the intensity of the third band similar to that observed for Cd(II), which could suggest the same binding pattern [27] for Cd(II) and Cu(II). However, a bathochromic shift of the first and second bands, a decrease in the intensity of the 1st band and an increase in the intensity of the second band are also observed with the addition of Cu(II) (Figure 5), which seems to indicate that the complexation interactions could differ for both metals. Note that for these UV-Vis titration experiments, the molar concentrations of both metals in solution are the same, and the molar concentration of ligand is less than or approximately equal to that of the metals. Thus, under these conditions, only 2:1 (metal: ligand) or 1:1 complexes are expected. Further studies will be conducted to elucidate the structure of the complexes. In general, the addition of increasing amounts of Cd(II) promotes an increase in band intensity between 313 and 370 nm, accompanied by a decrease in intensity for wavelengths between 250 and 313 nm, making it possible to identify an isosbestic point at 313 nm ( Figure 5). In turn, the addition of the same increasing amounts of Cu(II) causes an increase in the intensity of the third band similar to that observed for Cd(II), which could suggest the same binding pattern [27] for Cd(II) and Cu(II). However, a bathochromic shift of the first and second bands, a decrease in the intensity of the 1st band and an increase in the intensity of the second band are also observed with the addition of Cu(II) ( Figure 5), which seems to indicate that the complexation interactions could differ for both metals. Note that for these UV-Vis titration experiments, the molar concentrations of both metals in solution are the same, and the molar concentration of ligand is less than or approximately equal to that of the metals. Thus, under these conditions, only 2:1 (metal: ligand) or 1:1 complexes are expected. Further studies will be conducted to elucidate the structure of the complexes.

X-ray Crystallography
The structure was solved by direct methods using SHELXT-2014/5 [29]. Refinements were carried out with SHELXL-2018/3 [30] by full-matrix least-squares on F 2 , with anisotropic displacement parameters for all non-hydrogen atoms (CCDC 2063726 for details regarding the crystallographic analysis procedures and also for detailed crystal data). All hydrogen atoms could be located on a difference Fourier synthesis; their positions were refined as riding on parent atoms with an isotropic temperature constrained to those of their parent atoms using SHELXL-2018/3 defaults [30], except that of the amino group that is involved in hydrogen bonding, which had its position freely refined with an isotropic displacement factor constrained to 1.2× that of the parent N atom. The CF 3 group is disordered over two positions with occupancies close to 50%. The final quality factors of the refinement were R 1 (I > 2σ) = 0.0317, wR all = 0.0921 and GOF = 1.067 for 3097 for independent reflections and 221 refined parameters.

Metal Chelating Activity
3-((5-(trifluoromethyl)-1,3,4-thiadiazol-2-yl)amino)benzo[d]isothiazole 1,1-dioxide (AL14) was tested for its Cd(II) chelating activity, at different concentrations (1-20 mM). The chelating activity of AL14 was also assessed in separate experiments towards other potentially competing metal cations (Cu(II) and Fe(II)). The metal chelating activities were evaluated by spectrophotometry, using selective chelating indicators that produce coloured complexes, following methods described in the literature for Cu(II) and Fe(II) [31] and adopting the method described by Ahmed and Chowdhury [32] for Cd(II), with some adjustments for 96-well plates. Thus, the metal ion chelating activities were determined by measuring the colour changes due to the Cd(II)/5,7-dibromo-8-hydroxyquinoline (DBHQ) complex (at 396 nm) [32], Cu(II)/pyrocatechol violet (PV) complex (at 632 nm), and Fe(II)/ferrozine complex (at 562 nm) [17]. The capacity of the tested compound to chelate the metals should be reflected in a decrease in absorbance at each corresponding wavelength. The chelating activity was calculated using the Equation (1), where A blank and A sample correspond to the absorption of the solution without and with the ligand, respectively.

Conclusions
In short, this work unveils a new compound derived from saccharin capable of selectively chelating Cd(II), compared to Cu(II) and Fe(II). 3-((5-(trifluoromethyl)-1,3,4thiadiazol-2-yl)amino)benzo[d]isothiazole 1,1-dioxide (AL14) was analyzed in detail and its structure confirmed by 1D NMR ( 1 H and 13 C), 2D NMR (TOCSY, HSQC, and HMBC), X-ray crystallography, HRMS-ESI + and UV-Vis. In these experiments, the maximum chelating activity for Cd(II), 69.0 ± 3.3%, was achieved for [AL14] = 20 mM and [Cd] = 9 mM, without previous contact time. The concentration of ligand capable of removing 50% of Cd(II) concentration in solution (IC 50 ) is 7.857 mM. Reduced or no activity for Cu(II) and Fe(II) was observed, respectively. These are the first studies revealing the potential of this compound for selective Cd(II) chelation. Additional studies will be carried out, considering other environmentally relevant metal ions to assess their possible interference with the chelating capacity of this new and relatively low-cost ligand.