Thiourea Organocatalysts as Emerging Chiral Pollutants: En Route to Porphyrin-Based (Chir)Optical Sensing

Environmental pollution with chiral organic compounds is an emerging problem requiring innovative sensing methods. Amino-functionalized thioureas, such as 2-(dimethylamino)cyclohexyl(3,5-bis(trifluoromethyl)phenyl)thiourea (Takemoto’s catalyst), are widely used organocatalysts with virtually unknown environmental safety data. Ecotoxicity studies based on the Vibrio fischeri luminescence inhibition test reveal significant toxicity of Takemoto’s catalyst (EC50 = 7.9 mg/L) and its NH2-substituted analog (EC50 = 7.2–7.4 mg/L). The observed toxic effect was pronounced by the influence of the trifluoromethyl moiety. En route to the porphyrin-based chemosensing of Takemoto-type thioureas, their supramolecular binding to a series of zinc porphyrins was studied with UV-Vis and circular dichroism (CD) spectroscopy, computational analysis and single crystal X-ray diffraction. The association constant values generally increased with the increasing electronwithdrawing properties of the porphyrins and electron-donating ability of the thioureas, a result of the predominant Zn· · ·N cation–dipole (Lewis acid–base) interaction. The binding event induced a CD signal in the Soret band region of the porphyrin hosts—a crucial property for chirality sensing of Takemoto-type thioureas.


Introduction
The production of chiral chemicals is rapidly growing to satisfy the continuously increasing demand in various industrial and medicinal fields. Enantiomerically pure compounds often show improved bioactivity, fewer adverse effects, and increased selectivity over their achiral or racemic counterparts. More than 50% of pharmaceuticals and around 30% of pesticides are chiral, and their numbers are steadily growing [1][2][3]. An adverse effect of this process has increased the amount of pollution caused by chiral chemicals, representing a potential threat for ecosystems [4][5][6][7]. However, noteworthy ecotoxicology data are frequently unavailable and the environmental fate remains unclear for numerous artificial chiral compounds. The alarming increase in pollution calls for the development of innovative sensing methods to detect chiral pollutants in the natural environment [8,9]. Notably, a holistic approach for their detection should comprise both chemoselectivity and chirality sensing since opposite enantiomers may have different ecotoxicity, accumulation, and biodegradation rates. It turns out that the application of supramolecular chemistry [10][11][12], which relies on the formation of host-guest complexes between a sensor (host) and an analyte (guest), is an appealing direction to develop effective sensory systems. In this regard, porphyrins represent a family of unique sensing materials, which can effectively detect nonchiral and chiral analytes upon deposition onto a solid-state support [13,14]. In case of chiral analytes, simultaneous chirality sensing is possible due to chirality transfer phenomena (also designated as supramolecular chirogenesis) [15]. The binding event, most commonly occurring via coordination of a specific functional group in a chiral analyte to a metal ion in the porphyrin, produces a noticeable (chir)optical response in circular dichroism (CD) spectra. The produced CD signal can usually be correlated with the chirality of the guest, based on the well-defined structure of the host-guest complex [16][17][18][19]. Although this approach has been frequently applied to determine the absolute configuration of various chiral organic compounds, the design of porphyrin-based sensors for chemoselective detection of a specific chiral pollutant remains a challenging task.
As a rule, chiral pollutants are structurally diverse organic compounds containing multiple functional groups, which could potentially act as competitive binding sites and be involved in various non-covalent interactions. Such diversity could result in poorly interpretable net (chir)optical outcomes due to the generation of multiple structurally different host-guest assemblies upon interaction with a porphyrin host. The effects of various functional groups in a polyfunctionalized analyte on its (chir)optical response have not been investigated in detail and represent an arduous task in view of the tremendous structural diversity. Fortunately, the most common structural features can be outlined in the majority of typical chiral pollutants to simplify the problem. (1) Nitrogen-containing molecules are prevalent among pharmaceuticals and agrochemicals [20][21][22], and basic nitrogen moieties are therefore able to serve as privileged binding sites to zinc porphyrin-based sensors due to strong Zn· · · N cation-dipole interaction [23][24][25]. (2) Additional functional groups, which can act as a secondary binding site or participate in other non-covalent interactions (such as hydrogen bonding), are also common [26][27][28], along with (3) aromatic rings decorated with electron-donating/withdrawing substituents. While factor (1) is wellstudied, we assume that the impact of (2) and (3) on the key Zn· · · N binding event could be revealed by performing a systematic study with a series of structurally similar model compounds to "mimic" the organization of typical polyfunctionalized chiral pollutant. For this purpose, we selected a family of chiral analytes comprising 2-aminocyclohexyl arylthioureas 1a-d (Figure 1b). This was to perform binding studies with a series of zinc porphyrin hosts (Figure 1a), to assess the influence of additional functional groups and electronic effects, and to reveal the most suitable host-guest combinations exhibiting the strongest (chir)optical responses for reliable solution-phase detection by UV-Vis and CD spectroscopy. Additional information was derived from crystal structure determination and DFT calculations. Another motivation to test the (chir)optical detection of compounds 1a-d as model analytes is due to their widespread use as chiral organocatalysts. Enantioselective organocatalysis is believed to be a sustainable and world-changing chemical innovation, which has been highlighted by IUPAC as one of the "top ten emerging technologies in chemistry" in 2019 [29]. Since the pivotal discoveries of Schreiner [30], Jakobsen [31], and Takemoto [32], thioureas have found widespread use as prominent hydrogen-bonding organocatalysts [32][33][34]. They are used to prepare diverse chiral materials [33,35,36], including stereoselective ring-opening polymerization for the production of biodegradable polymers [37][38][39]. According to the SciFinder database [40], the parent Takemoto's catalyst 1d has been mentioned in 406 documents, including 44 patents, emphasizing its prominence also for commercial applications. In general, the thiourea catalysts are often referred to as a safer and sustainable alternative to the transition metal catalysts, in particular, because of the overstated toxicity of transition metal compounds [41,42]. However, the evidence for the environmental safety of organocatalysts is currently scarce [43]. The cytotoxic effect was recently revealed for a 3,5-bis(trifluoromethyl)phenyl thiourea derivative [44] that raised a reasonable concern about its potential harm. Here we report the results of an ecotoxicological evaluation of thioureas 1a-d, based on the Vibrio fischeri (also known as Aliivibrio fischeri) bioluminescence inhibition test [45]. Another motivation to test the (chir)optical detection of compounds 1a-d as model analytes is due to their widespread use as chiral organocatalysts. Enantioselective organocatalysis is believed to be a sustainable and world-changing chemical innovation, which has been highlighted by IUPAC as one of the "top ten emerging technologies in chemistry" in 2019 [29]. Since the pivotal discoveries of Schreiner [30], Jakobsen [31], and Takemoto [32], thioureas have found widespread use as prominent hydrogen-bonding organocatalysts [32][33][34]. They are used to prepare diverse chiral materials [33,35,36], including stereoselective ring-opening polymerization for the production of biodegradable polymers [37][38][39]. According to the SciFinder database [40], the parent Takemoto's catalyst 1d has been mentioned in 406 documents, including 44 patents, emphasizing its prominence also for commercial applications. In general, the thiourea catalysts are often referred to as a safer and sustainable alternative to the transition metal catalysts, in particular, because of the overstated toxicity of transition metal compounds [41,42]. However, the evidence for the environmental safety of organocatalysts is currently scarce [43]. The cytotoxic effect was recently revealed for a 3,5-bis(trifluoromethyl)phenyl thiourea derivative [44] that raised a reasonable concern about its potential harm. Here we report the results of an ecotoxicological evaluation of thioureas 1a-d, based on the Vibrio fischeri (also known as Aliivibrio fischeri) bioluminescence inhibition test [45].

Materials and Methods
General methods. UV-Vis absorption spectra were recorded on a Jasco V-730 doublebeam spectrophotometer (JASCO International Co., Ltd., Tokyo, Japan) in a 1 cm thermally stabilized screw-cap quartz cuvette with a septum cap. CD spectra were recorded on a Jasco J-1500 spectrophotometer (JASCO International Co., Ltd., Tokyo, Japan) in a 1 cm screw cap quartz cuvette in analytical grade CH 2 Cl 2 at 293 K. The data acquisition was performed in the 375-475 nm range with the scanning rate of 50 nm/min, bandwidth of 2.6 nm, response time of 4 s, and accumulations in three scans. 1 H NMR spectra were recorded in CDCl 3 at 293 K, using a QCI CryoProbe on a Bruker AVANCE III 800 MHz spectrometer (Bruker Corporation, Billerica, MA, USA). The number of scans was in the range of 8 to 64 scans and was optimized for the samples to obtain a signal to noise ratio of 250 in the recorded spectra. A relaxation delay of 5 s was used. The acquisition time was set to 2.4 s. The spectra were processed in MestReNova 14.2 software and zero filled to 128k points to obtain chemical shifts for finding the dimerization constants. The chemical shifts (δ) were reported in ppm and referenced to a CHCl 3 residual peak at 7.26 ppm.
Porphyrins P1-P8, except for P3, were prepared by insertion of zinc ion into the corresponding free base porphyrins by following the standard experimental protocol [48,49]. Starting free base porphyrins and zinc(II) tetraphenylporphyrin (ZnTPP, P3) were purchased from PorphyChem. Porphyrin P9 was prepared as previously described [50]. The purity and chemical identity of the prepared Zn porphyrins was validated by NMR and UV-Vis spectroscopy.
Spectroscopic Titrations. All the solutions were prepared and mixed by using properly calibrated analytic glassware (Hamilton ® Gastight syringes, volumetric flasks, Reno, Nevada, USA). All weights were balanced with a Radwag MYA 11.4 microbalance (accuracy ± 6 µg). The concentration of zinc porphyrin was held constant throughout the titration sequence. The titration data were fitted by using the online software Bindfit [51][52][53]. The UV-Vis spectrophotometric titration experiments were performed in analytical grade CH 2 Cl 2 . To a solution of zinc porphyrin, a solution of guest (dissolved in a stock solution of the host to keep the concentration of the host constant) was added portion-wise using a gastight syringe at 293 K. The corresponding changes in bathochromic shift of the Soret band were monitored at different concentrations of the guest.
Self-association of thioureas 1a and 1c has been studied by measuring changes in the chemical shifts of diagnostic protons in the 1 H NMR spectra upon dilution [54,55]. To determine the dimerization constants, the experimental data were fitted using the numpy (1.18.5) and scipy (1.

4.1) libraries of Python 3 (see the Supplementary Materials for details).
Single crystal X-ray analysis. Crystals of the (R,R)-1b·P5 complex were obtained by slow solvent evaporation from an equimolar mixture of (R,R)-1b and P5 (0.005 mmol of each), dissolved in dichloromethane/methanol (v:v, 2:1, 1.5 mL). The single-crystal X-ray data of complex (R,R)-1b·P5 were acquired using a dual-source Rigaku SuperNova diffractometer equipped with an Atlas detector and an Oxford Cryostream cooling system using mirror-monochromated Cu-K α radiation (λ = 1.54184 Å). Data collection and reduction for all complexes were performed using the program CrysAlisPro [56] and the Gaussian face-index absorption correction method was applied [56]. The structures were solved with Direct Methods (SHELXS) [57][58][59] and refined by full-matrix least-squares based on F 2 using SHELXL-2015 [57][58][59]. Non-hydrogen atoms were assigned anisotropic displacement parameters unless stated otherwise. The hydrogen atoms bonded to nitrogens were located from Fourier difference maps and refined with an N−H distance restraint of approximately 0.96 Å. Other hydrogen atoms were placed in idealized positions and included as riding. The isotropic displacement parameters for all H atoms were constrained to multiples of the equivalent displacement parameters of their parent atoms with U iso (H) = 1.2 U eq (parent atom). A few reflections with large discrepancies between the calculated and observed structure factors have been omitted from the least-squares refinement as outliers. The X-ray single crystal data and experimental details as well as CCDC number are given below.
Toxicity Evaluation. Acute bioluminescence inhibition assay (exposure time 30 min) with naturally bioluminescent bacteria Vibrio fischeri was performed at ambient temperature (~293 K) on white sterile 96-well polypropylene microplates (Greiner Bio-One GmbH, Frickenhausen, Germany) following the Flash assay protocol (ISO, 2010) [87]. The bacterial suspension used for the toxicity measurements was prepared from freeze-dried bacteria originating from a Vibrio fischeri reagent (Aboatox, Turku, Finland). As aminofunctionalized thioureas are poorly soluble in water their stock solutions were prepared in methanol (final concentration of MeOH in the toxicity test was 1.5% that is a not toxic concentration to Vibrio fischeri) and then 2% NaCl was added. The highest tested concentration for the test chemicals was 50 mg/L, except for Takemoto's catalyst for which it was 6.45 mg/L. Briefly, 100 µL of the test solution in 3% MeOH and 2% NaCl was pipetted into each well, which was supplemented with 100 µL of bacterial suspension in 2% NaCl by automatic dispensing in a Microplate Luminometer Orion II (Berthold Detection Systems, Pforzheim, Germany) testing chamber. All the chemicals were tested on three different days, in 5-7 dilutions in two replicates for each chemical. The controls, both negative (1.5% MeOH in 2% NaCl) and positive (ZnSO 4 , prepared from ZnSO 4 ·7H 2 O), were included in each run. The inhibition of bacterial bioluminescence by the tested compounds was calculated as a percentage of the unaffected control (1.5% MeOH in 2% NaCl) after 30 min contact time. Inhibition of bacterial luminescence (INH%) by the analyzed compounds was calculated as follows: where KF (correction factor) characterizes the natural loss of bioluminescence of the control (i.e., bacterial suspension in 1.5% MeOH in 2% NaCl). IC 0 and IT 0 are the maximum values of bioluminescence during the first 5 s after dispensing 100 µL of test bacteria to 100 µL of control and test sample, respectively. IC 30 and IT 30 are the respective bioluminescence values after 30 min. The toxicity values (30-min EC 50 , which is the concentration of a compound reducing the bioluminescence by 50% after contact time of 30 min) and their confidence intervals were determined from dose-response curves based on the nominal exposure concentrations using the log-normal model of MS Excel macro Regtox [88].

Toxicity Studies
In the current study, amino-functionalized thioureas (1a-d, Figure 1b) were screened for toxicity using a Vibrio fischeri 30-min kinetic luminescent bacteria test according to the Flash-test protocol (see above). Vibrio fischeri is a naturally bioluminescent marine bacterium, thus being an environmentally relevant test organism. Moreover, these bacteria are important ecosystem members as biodegraders. The Vibrio fischeri bioluminescence inhibition assay is a rapid, cost-efficient, and sensitive analytical tool, which has been widely used for toxicity testing of different types of chemicals [89,90] and polluted environmental samples (such as wastewaters and sediments) [91]. Importantly, this bioassay data have widely been used for the quantitative structure-activity relationship (QSAR) models analysis to predict the toxicity of organic chemicals by their chemical structures [92]. The decrease in bacterial luminescence results from the chemical's adverse effects on the bacterial membrane and consequently their energy metabolism and occurs after brief contact with toxicants (ranging from seconds to minutes depending on the compounds) [93].
The experimentally determined 30-min EC 50 values of Vibrio fischeri for aminofunctionalized thioureas are presented in Table 1. Based on the simplified hazard classification scheme described in [92] the studied chemicals can be ranked according to the respective 30-min EC 50 values as follows: ≤1 mg/L = very toxic; >1-10 mg/L = toxic; >10-100 mg/L = harmful; >100 mg/L = "not classified / not harmful". As a result, Takemoto's catalyst (S,S)-1d and its NH 2 -substituted siblings ((R,R)-and (S,S)-1a) were found to be ranked as toxic analogously to the used positive control (ZnSO 4 ). At the same time, phenyl-and 3,5-dimethylphenyl thioureas ((R,R)-1b and 1c) showed no inhibitory properties up to the maximum concentration tested (EC 50 > 50 mg/L). It is of note that no significant difference in the EC 50 values was observed for both (R,R)-and (S,S)-enantiomers of 1a. All tested compounds with the CF 3 -group had a similar slope in their dose-response curve (Figure 2), indicating a similar mechanism of the toxic action.  50 , mg/L) of amino-functionalized thioureas 1a-d and the used positive control (ZnSO 4 ) to Vibrio fischeri a . 1 Note the logarithmic scale of x-axis.  Table 1. Note the logarithmic scale of x-axis.

30-min EC 50 , mg/L 95% Confidence Interval
The toxic effect of thioureas 1a and 1d evidently arises from the 3,5-bis(trifluoromethyl) phenyl group [94]. Importantly, the same moiety is crucial to enhance the organocatalytic activity and selectivity of thiourea catalysts [95][96][97]. The ecotoxicity studies presented above, along with steadily expanding applications of thiourea catalysts, highlight their status as plausible emerging chiral pollutants, for which detection methods in solution have yet to be developed.

Binding and Structural Studies
Complexation of 1a-d with zinc porphyrins P1-P9 is a reversible process that occurs via coordination of the amino group in 1a-d to zinc ion in a porphyrin host (Figure 3a). This produces a measurable spectral change for the detection of amino-functionalized thioureas 1a-d in solution. This complexation can conveniently be followed by conventional UV-Vis spectroscopy and results in corresponding bathochromic shifts of the porphyrin Soret and Q bands with the representative example of 1a·P5 complex shown in Figure 3b (see the Supplementary Materials for other host-guest systems).
The structures of the complexes formed are most reliably identified and described by crystallography and DFT geometry calculations, respectively. The crystallographic data for 1b·P5 complex provides proof for the 1:1 complex formation via coordination of the amino group in 1b to the zinc ion of porphyrin P5 (Figure 4). The guest thiourea is resting in a favorable syn-anti conformation with respect to the N-H orientation in the thiourea moiety [98]. One of the N-H bonds in the NH 2 group is stabilized by the sulfur atom of 1b with a N· · · S distance of 3.266 Å and a contact angle of 160.6 • leading to a short intermolecular N-H···S hydrogen bond. The phenyl ring in 1b is tilted out of plane of the thiourea unit with a torsional angle ϕ(C (=S) -N-C Ph -C Ph ) = 86.1 • . It is nearly perpendicular to the porphyrin plane and parallel to the neighboring aryl substituent in the porphyrin host, albeit the distance between the rings' centroids (~6 Å) is too high for any π-π or π-σ interactions between the aromatic moieties of the host and the guest to be involved [99].
Typically for zinc porphyrin complexes, the zinc ion is penta-coordinated and slightly displaced out of the mean porphyrin plane towards the nitrogen atom of the NH2 group, with a Zn⋯N distance of 2.131 Å. Coordination of the chiral guest 1b induces an asymmetric distortion of the porphyrin plane. Consequently, it resulted in reducing the symmetry for the D4h-symmetric porphyrin core to a C1 point group, which was confirmed using the normal-coordinate structural decomposition method (NSD) [100,101]     Although the solid-state structure explicitly confirmed the 1:1 complex formation, the analysis of spectroscopic titration data raised some concerns regarding the alleged involvement of more complex stoichiometry in solution [52]. For example, the titration . Displacement ellipsoid plot of the (R,R)-1b·P5 complex. Displacement ellipsoids are drawn at the 50% probability level. The co-crystallized CH 2 Cl 2 molecule has been omitted for clarity. Selected interatomic distances (Å): Zn1· · · N1 2.075(4), Zn1· · · N2 2.080(4), Zn1· · · N3 2.070(3), Zn1· · · N4 2.075(4), Zn1· · · N5 2.131(3).
Typically for zinc porphyrin complexes, the zinc ion is penta-coordinated and slightly displaced out of the mean porphyrin plane towards the nitrogen atom of the NH 2 group, with a Zn· · · N distance of 2.131 Å. Coordination of the chiral guest 1b induces an asymmetric distortion of the porphyrin plane. Consequently, it resulted in reducing the symmetry for the D 4h -symmetric porphyrin core to a C 1 point group, which was confirmed using the normal-coordinate structural decomposition method (NSD) [100,101] via the NSD online tool [102] (see the Supplementary Materials for details).
Although the solid-state structure explicitly confirmed the 1:1 complex formation, the analysis of spectroscopic titration data raised some concerns regarding the alleged involvement of more complex stoichiometry in solution [52]. For example, the titration curve for P5-1a host-guest system can be successfully fitted with either 1:1 or 1:2 binding isotherms (see the Supplementary Materials, Figures S14 and S15, Table S5). While the former yielded a K a value of 4180 ± 50 (with SSR error 2.8 × 10 −3 ), using the 1:2 isotherm gave stepwise association constants: K 1 = 3940 ± 20 and K 2 = 50 ± 10 (with SSR error 8.0 × 10 −4 ). The K 1 value remained close to this obtained with the 1:1 model and could be attributed to the dominant Zn· · · N interaction, while the small K 2 association constants could be related to weak binding of the second thiourea guest through hydrogen bonding. This is not surprising, taking into account the well-known self-aggregating behavior of thioureas in solution [54,[103][104][105][106]. Indeed, measuring the concentration dependence of chemical shifts in 1  The obtained K a values and absorption maxima in the UV-Vis spectra for all 25 hostguest complexes studied are summarized in Table 2. The knowledge of association constants is essential to select the porphyrin host producing the most significant analytical response in terms of sensitivity and selectivity. In addition, it provides a useful insight into the binding mechanism and nature of the supramolecular interactions involved, which are necessary prerequisites in the rational design of an efficient chemical sensor.
We have shown previously that the complexation of 1a-c with ZnTPP (P3) occurs predominantly via the amino nitrogen atom, while the thiocarbonyl group has a low binding affinity to the zinc ion in P3 [60]. Also, the values of association constants increased with rising the electron-donating ability of corresponding guests (1a < 1b < 1c) and the electron-withdrawing properties of the hosts (zinc(II) tetraphenylporphyrin > zinc(II) octaethylporphyrin), hence clearly indicating a predominantly electrostatic (Lewis acidbase) nature of the host-guest interaction. Since the association constant for coordination of 1a to ZnTPP (P3) did not exceed 2300 M −1 , we supposed that further increasing the electron-withdrawing properties of a porphyrin host could lead to even greater values of the association constants, and therefore to enhanced sensitivity of the guest's detection in solution. This trend can be explicitly revealed by measuring the corresponding association constants for a series of substituted ZnTPPs P1-P9 with steady elevation of the electrondeficiency at the zinc cation ( Figure 1b).
As expected, both 1b and 1c showed a gradual increase in the association constants with rising the electron-withdrawing properties of the hosts ( Table 2, lines 10-14 and 15-22, respectively). Within these series, as expected, the largest association constant of (1.41 ± 0.04) × 10 5 was determined for a combination of the most electron-donating guest 1c and the highly electron-deficient C 6 F 5 -substituted porphyrin P8 (Table 2, Table 2, lines 6 and 7). Considerably lower association constants were observed in these two particular cases compared to the extrapolation based on the Hammett plot ( Figure 5, black line). It is of note that the attenuation was even more substantial in the case of the more electron-deficient p-CN substituted porphyrin host P7 than p-CF 3 porphyrin P6. Table 2. Association constants (K a ), Hammett substituent constants (σ para ) for para substituted benzene rings in porphyrins P2-P7, and absorption maxima (λ max ) in UV-Vis spectra for complexes of thioureas 1a-d with zinc porphyrins P1-P9 measured in CH 2 Cl 2 .  [107]. b Errors are fitted for the 1:1 binding isotherm. c The host-guest system has been previously described [60]. d The association constant is too low for the UV-Vis spectroscopic titration measurement (n.d. = not determined).

Entry
The outliers are evidently due to the presence of strong electron-withdrawing groups (CF 3 and CN) in the aryl rings of both the hosts P7, P6, and the guest 1a, which should introduce a noticeable perturbation of the host-guest complex geometry and result in a considerable decrease in the corresponding association constants. Indeed, the DFT calculations showed a different geometry for the main conformer of 1a·P6 in comparison with the previously studied complex 1a·P3 [60] and significant overall change in the conformational composition of these two complexes. Thus, in the complex 1a·P3, the two most populated conformers (abundance 48.6% and 24.5% at 298 K) have a similar face-to-face orientation of one aryl of host P3 and another aryl of guest 1a [60] (Figure 6). On the contrary, a T-shaped orientation of aryl substituents was observed in two main conformers of 1a·P6 (abundance 46.6% and 37.9% at 298 K) (see Figure 6 and Table S28 in the Supplementary Materials). The differences in geometries and conformational composition also result in elongation of the Zn-N guest bond in 1a·P6 compared to 1a·P3 (weighted-average values 2.155 Å and 2.145 Å, respectively; see Table S29 in the Supplementary Materials). This explains the weaker binding for the 1a·P6 complex ( Table 2, entries 3 and 6). two particular cases compared to the extrapolation based on the Hammett plot ( Figure 5, black line). It is of note that the attenuation was even more substantial in the case of the more electron-deficient p-CN substituted porphyrin host P7 than p-CF3 porphyrin P6. Figure 5. Hammett plots of logKa vs. σpara constants for coordination of 1a (black points, outliers are marked with red rim), 1b (red points), and 1c (blue points) to zinc tetraphenylporphyrins P2-P7 with para substituents in the benzene rings.
The outliers are evidently due to the presence of strong electron-withdrawing groups (CF3 and CN) in the aryl rings of both the hosts P7, P6, and the guest 1a, which should introduce a noticeable perturbation of the host-guest complex geometry and result in a considerable decrease in the corresponding association constants. Indeed, the DFT calculations showed a different geometry for the main conformer of 1a•P6 in comparison with the previously studied complex 1a•P3 [60] and significant overall change in the conformational composition of these two complexes. Thus, in the complex 1a•P3, the two most populated conformers (abundance 48.6% and 24.5% at 298 K) have a similar face-to-face orientation of one aryl of host P3 and another aryl of guest 1a [60] (Figure 6). On the contrary, a T-shaped orientation of aryl substituents was observed in two main conformers of 1a•P6 (abundance 46.6% and 37.9% at 298 K) (see Figure 6 and Table S28 in the Supplementary Materials). The differences in geometries and conformational composition also result in elongation of the Zn-Nguest bond in 1a•P6 compared to 1a•P3 (weighted-average values 2.155 Å and 2.145 Å, respectively; see Table S29 in the Supplementary Materials). This explains the weaker binding for the 1a•P6 complex ( Table 2, entries 3 and 6).
The topological analysis of electron density in the complex 1a•P3 with the aid of the quantum theory of atoms in molecule (QTAIM) approach reveals many non-covalent interactions between the host and the guest. Despite a short distance, ca 3.8 Å between centroids [60] of the close-by phenyls of the guest 1a and host P3, and the presence of a C•••C bond path between the aryl carbon atoms belonging to the different rings, the electron density at the bond critical point is 0.008 a.u. (see Figure 6 and Table S30 in the Supplementary Materials). Such low electron density is characteristic of a weak and unstable ππ interaction in 1a•P3. [108,109]  order stabilization energies of 2.90 kcal mol −1 , and, from the π-π stacking, the secondorder stabilization energy was 7.78 kcal mol −1 for 1a•P3 complex ( Figure 6 and Table S32 in the Supplementary Materials) [110]. The Zn⋯N second-order stabilization energies were 143.64 kcal mol −1 ( Table S32 in the Supplementary Materials). In the main conformers of complex 1a•P6, the CF3 groups in the host P6, and the guest 1a force the aryl substituents to adopt a T-shaped orientation (see Figure 6 and Table S31 in the Supplementary Materials). This agrees with the previous theoretical study where it was shown that an electronegative substituent makes the T-shaped orientation of aryls more favorable due to the exchange or dispersion of the component's contribution to the binding energy [111]. Here, the NBO partial charges are very similar on the host and guest aryls in both complexes (see Table S31 in the Supplementary Materials). The QTAIM approach proves the presence of σ/π interactions by the electron density at the bond critical point ρ(r) = 0.008 a.u. and the Laplacian of electron density, showing alternation in electronic charge, is positive. These characteristics are typical for such interactions [112].
Moreover, a weak dispersion and strong non-covalent interactions between the H⋯C, H⋯F, F⋯C, and S⋯H atoms provided additional stabilization of 1a•P6. The NBO analysis showed that the T-shaped orientation of aryls resulted in smaller values of the second-order stabilization energies from π-π stacking (1.90 kcal mol −1 ), compared to those of complex 1a•P3 (7.78 kcal mol −1 ). On the other hand, the non-covalent interactions between the H⋯C, H⋯F, F⋯C, and S⋯H atoms additionally stabilized the complex 1a•P6 by 7.58 kcal mol −1 . In contrast, in the 1a•P3 complex this energy was only 2.9 kcal mol −1 (see Table S32 in the Supplementary Materials). The Zn⋯N second-order stabilization energies The topological analysis of electron density in the complex 1a·P3 with the aid of the quantum theory of atoms in molecule (QTAIM) approach reveals many non-covalent interactions between the host and the guest. Despite a short distance, ca 3.8 Å between centroids [60] of the close-by phenyls of the guest 1a and host P3, and the presence of a C···C bond path between the aryl carbon atoms belonging to the different rings, the electron density at the bond critical point is 0.008 a.u. (see Figure 6 and Table S30 in the Supplementary Materials). Such low electron density is characteristic of a weak and unstable π-π interaction in 1a·P3. [108,109]. The QTAIM approach also reveals the presence of weak interactions between H···C, H···F, and F···C atoms in the aryls of the host-guest pair. Natural bond orbital (NBO) analysis confirmed the presence of weak stabilizing effects of the interactions between the same H···C, H···F, and F···C atoms with the estimated second-order stabilization energies of 2.90 kcal mol −1 , and, from the π-π stacking, the second-order stabilization energy was 7.78 kcal mol −1 for 1a·P3 complex ( Figure 6 and Table S32 in the Supplementary Materials) [110]. The Zn· · · N second-order stabilization energies were 143.64 kcal mol −1 (Table S32 in the Supplementary Materials).
In the main conformers of complex 1a·P6, the CF 3 groups in the host P6, and the guest 1a force the aryl substituents to adopt a T-shaped orientation (see Figure 6 and Table S31 in the Supplementary Materials). This agrees with the previous theoretical study where it was shown that an electronegative substituent makes the T-shaped orientation of aryls more favorable due to the exchange or dispersion of the component's contribution to the binding energy [111]. Here, the NBO partial charges are very similar on the host and guest aryls in both complexes (see Table S31 in the Supplementary Materials). The QTAIM approach proves the presence of σ/π interactions by the electron density at the bond critical point ρ(r) = 0.008 a.u. and the Laplacian of electron density, showing alternation in electronic charge, is positive. These characteristics are typical for such interactions [112].
Moreover, a weak dispersion and strong non-covalent interactions between the H· · · C, H· · · F, F· · · C, and S· · · H atoms provided additional stabilization of 1a·P6. The NBO analysis showed that the T-shaped orientation of aryls resulted in smaller values of the secondorder stabilization energies from π-π stacking (1.90 kcal mol −1 ), compared to those of complex 1a·P3 (7.78 kcal mol −1 ). On the other hand, the non-covalent interactions between the H· · · C, H· · · F, F· · · C, and S· · · H atoms additionally stabilized the complex 1a·P6 by 7.58 kcal mol −1 . In contrast, in the 1a·P3 complex this energy was only 2.9 kcal mol −1 (see Table S32 in the Supplementary Materials). The Zn· · · N second-order stabilization energies were 139.08 kcal mol −1 , that is, 4.56 kcal mol −1 smaller compared to complex 1a·P3 (see Table S32 in the Supplementary Materials). However, the overall stabilizing effect was about 5.76 kcal mol −1 smaller than that of the complex 1a·P3. Therefore, we can conclude that the cumulative effect of the different conformational composition and additional interactions were responsible for the observed attenuation of the binding strength of host-guest pairs with electron-withdrawing groups on the aryls.
However, the observed attenuation of binding of 1a to electron-deficient P6 and P7 could be surpassed with even more electron-deficient porphyrin hosts, such as P8 and P9 (Table 2), by increasing the strength of the dominant Zn· · · N interaction. Indeed, porphyrins P8 and P9 resulted in remarkably high association constants of (1.27 ± 0.02) × 10 4 and (5.2 ± 0.6) × 10 5 , respectively ( Table 2 lines 8 and 9). Similar to the 1c·P8 system, the case of 1a·P9 represented another extreme K a value, a consequence of the electronwithdrawing character and the non-planar saddle distortion [113][114][115] of P9, which additionally enhanced the binding of the axial ligands [49].
Replacing the NH 2 group in 1a with the NMe 2 group in Takemoto's catalyst 1d weakened the binding strength considerably due to a sterically less accessible nitrogen lone pair [116,117]. Thus, adding 1d to a solution of P3 caused no significant change in the porphyrin UV-Vis spectrum ( Table 2, line 23). However, by taking advantage of the trends revealed for 1a, we supposed that P8 and P9 could again be the preferred hosts in the case of 1d as well. Although planar P8 afforded a relatively small value of the association constant being around 450 M −1 , non-planar P9 with its eight additional bromine atoms resulted in the considerable increase in K a of up to (1.16 ± 0.07) × 10 4 .

Circular Dichroism Spectra
Coordination of a chiral guest to a planar and achiral porphyrin host typically induces a notable CD signal in the region of the porphyrin Soret band and allows the guest's chirality to be sensed. This was the case for almost all the host-guest systems studied (Table 3; Figure 7, see also Supplementary Materials), with only two exceptions of the CD-silent complexes (R,R)-1a·P7 and (S,S)-1d·P9. The CD spectra were measured at the end point of UV-Vis titration experiments with a high molar excess of the thiourea guests that corresponded to 87−99% conversion of unligated zinc porphyrin into the complex, as calculated by the values of the association constants. The (chir)optical outcome is clearly specific for a certain host-guest combination, with respect to both the amplitude and sign of observed Cotton effects (CE). Such variability is not unexpected in the view of the complex origin of net CD signal [26,69,101,[118][119][120]. Enantiomers of compound 1a display CD signal in the far-UV region with λ max of 253 nm and 308 nm and intensities of 15 M −1 ·cm −1 and 28 M −1 ·cm −1 , respectively (see Figure S86 in the Supplementary Materials). Table 3. CD data for the complexes of zinc porphyrins P1-P9 with thioureas 1a-d measured in CH 2 Cl 2 .

Entry
Complex The host-guest system has been previously described [60].
Chemosensors 2021, 9, x FOR PEER REVIEW 13 of 20 Replacing the NH2 group in 1a with the NMe2 group in Takemoto's catalyst 1d weakened the binding strength considerably due to a sterically less accessible nitrogen lone pair [116,117]. Thus, adding 1d to a solution of P3 caused no significant change in the porphyrin UV-Vis spectrum ( Table 2, line 23). However, by taking advantage of the trends revealed for 1a, we supposed that P8 and P9 could again be the preferred hosts in the case of 1d as well. Although planar P8 afforded a relatively small value of the association constant being around 450 M −1 , non-planar P9 with its eight additional bromine atoms resulted in the considerable increase in Ka of up to (1.16 ± 0.07) × 10 4 .

Circular Dichroism Spectra
Coordination of a chiral guest to a planar and achiral porphyrin host typically induces a notable CD signal in the region of the porphyrin Soret band and allows the guest's chirality to be sensed. This was the case for almost all the host-guest systems studied (Table 3; Figure 7, see also Supplementary Materials), with only two exceptions of the CDsilent complexes (R,R)-1a•P7 and (S,S)-1d•P9. The CD spectra were measured at the end point of UV-Vis titration experiments with a high molar excess of the thiourea guests that corresponded to 87−99% conversion of unligated zinc porphyrin into the complex, as calculated by the values of the association constants. The (chir)optical outcome is clearly specific for a certain host-guest combination, with respect to both the amplitude and sign of observed Cotton effects (CE). Such variability is not unexpected in the view of the complex origin of net CD signal [26,69,101,[118][119][120]. Enantiomers of compound 1a display CD signal in the far-UV region with λmax of 253 nm and 308 nm and intensities of 15 M −1 •cm −1 and 28 M −1 •cm −1 , respectively (see Figure S86 in the Supplementary Materials). Previously, we showed that conformational changes in 1a produced different CD outcomes in the 1a•P3 complex [60]. The overall CD spectrum profile, consisting of a weak positive and relatively strong negative CEs (Figure 7; Table 3, line 3), was determined as a Boltzmann average of the separate conformer's inputs and perfectly matched the experimental spectrum. Analogously, it is reasonable to assume that the CD spectra observed Previously, we showed that conformational changes in 1a produced different CD outcomes in the 1a·P3 complex [60]. The overall CD spectrum profile, consisting of a weak positive and relatively strong negative CEs (Figure 7; Table 3, line 3), was determined as a Boltzmann average of the separate conformer's inputs and perfectly matched the experimental spectrum. Analogously, it is reasonable to assume that the CD spectra observed for the sibling complexes simply reflect the differences in the respective conformational compositions, mostly determined by the guest molecules as components with a higher degree of conformational freedom. Indeed, despite the rather specific (chir)optical outcomes observed in these supramolecular complexes (Figure 7, Table 3), some generalizations can be tentatively outlined, supporting this hypothesis. In the series of complexes with structurally similar p-substituted ZnTPP hosts (P2-P7), the (chir)optical outcome is mostly determined by the guest, while the porphyrin host has a somewhat secondary impact. Thus, thioureas 1b and 1c are inclined to induce monosignate positive CEs (Figure 7, Table 3, lines 10-21). However, it can be noted that in the case of 1a, the rise of electronegativity in the porphyrin binding site results in a positive monosignate signal to transform into a bisignate CD signal (see Figure S84 in the Supplementary Materials). Moreover, the complexes of 1a with the most electronegative porphyrins of the selection P2 and P1 produce a monosignate negative CD signal only.
It is worth noting that the amplitudes of the induced CD signals do not correlate with the values of association constants, e.g., the complex (R,R)-1c·P5 gives virtually the same maximal CE intensity (+23 M −1 ·cm −1 ; line 18 in Table 3) as that of the complex (R,R)-1c·P8 (+21 M −1 ·cm −1 ; line 21 in Table 3) possessing an order of magnitude greater association constant (see Table 2, lines 18 and 22). While the maximum CE intensity was found to be ±25 M −1 ·cm −1 , CD silent spectra were observed for (R,R)-1a·P7 and (S,S)-1d·P9, apparently due to mutual compensation of the oppositely-signed CD signals of different host-guest conformers. Unfortunately, the strongly complexing porphyrins P8 and P9 produce rather modest CD responses for the analytes of major concern due to their toxicity (1a and 1d). This implies that further structural modifications of these hosts are required for better sensing adaptation, to enhance the (chir)optical outcome and preserve high association constant values. Highly electron-deficient porphyrins P8 and P9 can be considered as good starting scaffolds for such modifications.

Conclusions
Given the toxic effect revealed for 3,5-bis(trifluoromethyl)phenyl)-substituted thioureas 1a and 1d (Takemoto's catalyst) in the Vibrio fischeri luminescence inhibition test, these conventional organocatalysts and similar compounds might pose an environmental pollution risk. Although additional ecotoxicology and biodegradation studies are required to clearly manifest their ecological impact, 1a and 1d can be considered as emerging chiral pollutants, for which a reliable instrumental detection method must be developed.
We have addressed this important environmental issue for the first time. Thus, the solution detection of 1a-d and similar nitrogen-containing chiral pollutants could be based on supramolecular binding with suitable zinc porphyrin hosts in which the Zn· · · N cationdipole interaction is dominant, and the complex stability increases with the rising electronwithdrawing properties of the porphyrin host. As a first step in this direction, we have performed selective screening of several zinc porphyrins P1-P9 with a gradual increase in the electron-withdrawing properties to identify the best sensory candidates in terms of the highest values of its association constants (in range from 10 2 to 10 5 M −1 ) and (chir)optical response (from negative to positive CE). For the target analytes 1a and 1d, the electrondeficient and non-planar porphyrin P9 was revealed as the strongest binder, which could be particularly suitable for further practical adaptations. Additional non-covalent interactions, such as weak π-π interactions provided by the aromatic groups or hydrogen bonding ensured by the thiourea moiety, might be present in the host-guest systems studied, and could be used to enhance the sensory sensitivity and selectivity. However, based on our study, we recommend using porphyrins P2 and P3 to detect of chiral pollutant 1a due to the strong and specific (chir)optical outcomes. To detect chiral pollutant 1d, porphyrin P8 gives the best (chir)optical response out of our current porphyrin library.
It was found that the (chir)optical outcome was specific for certain host-guest combinations, with respect to the amplitude, sign, and the number of observed CEs induced in the Soret band region with the maximal CE intensity of ±25 M −1 ·cm −1 . For a better and clearly interpretable CD response, further structural modification of the parent hosts P8 and P9 is needed to attenuate the adverse effects caused by the guests' conformational flexibility. For this purpose, introducing additional binding point(s) specific to the thiourea functionalities could be one of the host's further developments. The design and investigation of the next generation of porphyrin hosts based on these principles, suitable for the effective detection of chiral pollutants in real-world environments, are currently in progress at our laboratory. A comprehensive analysis of CD induction phenomena in these systems, crucial for the sensor design, will be reported in due course.