Synthesis, crystal structure, photoluminescence and catalytic properties of a novel cuprous complex with 2,3-pyrazinedicarboxylic acid ligands

A copper (I) polymer, [Cu2Mg(pzdc)2(H2O)5•2H2O]n (pzdc = 2,3-Pyrazinedicarboxylic acid), was synthesized by solvothermal method. The complex was characterized using X-ray diffraction (XRD), fourier transform infrared spectroscopy (FT-IR), ultraviolet-visible spectrophotometry (UV-Vis), and element analysis. X-ray crystal structure analysis reveals that the complex is a two-dimensional coordination polymer. The photophysical and luminescent properties of the complex were investigated. At room temperature, the complex exhibits reversible double strands cyclic voltammogram and displays efficient blue emission with peak maxima at 468 nm. Catalytic liquid phase oxidation of dyes and glyphosate was carried out using the copper (I) polymer as catalyst and H2O2 as oxidant. Degradation efficiencies were evaluated by varying the reaction conditions (i.e. illumination and oxidant). In the degradation reactions, the polymer exhibits high degradation efficiency within a short reaction time under the optimum reaction conditions. Furthermore, the reusability of the catalyst is excellent, showing no activity loss in four repeated cycles. The possible reaction mechanism catalyzed by the polymer was inferred on the basis of the results of electron spin resonance (ESR), electrochemical and ion chromatography analyses (IC).

commonly involved in the coordination. It should be emphasized that the copper (I) complex of the present study is a two-dimensional (2D) polymer with luminescent behavior. In addition, copper-based complexes have been used in a wide range of catalytic reactions [27][28][29] . With the facile change of Cu oxidation state, the Cu-based complexes can directly drive or catalyze many redox reactions. Also, because the complexes are insoluble, they can be easily separated and reused. The oxidation processes are eco-friendly because H 2 O 2 is commonly used as oxidant, with water being the only by-product. In this article, we report the outstanding photocatalytic performance of the copper (I) polymer in the degradation of dyes and glyphosate, and conduct discussion on the related mechanism. experimental Materials and methods. Reagent grade 2,3-pyrazinedicarboxylic acid, oxalyl dihydrazide, copper nitrate trihydrate, Mg(OH) 2 , hydrogen peroxide (30% solution), glyphosate, rhodamine B (RhB), methyl orange (MO) were all purchased from Shanghai sinopharm chemical reagent Co. Ltd. They were used without any further purification. In the studies, purified water was used as solvent.
The elemental analysis of C, H and N was performed on a model 2400 Perkin-Elmer analyzer. The IR spectra were recorded (KBr pellets) on a Nicolet 170SX spectrophotometer in the 4000-400 cm −1 region. The UV-Vis absorption spectra were recorded (BaSO 4 pellets) on a SHIMADZU UV-2600 UV-Vis spectrophotometer in the range of 200-700 nm. Powder X-ray diffraction (PXRD) measurements were performed at room temperature on a Philips X'pert MPD Pro X-ray diffractometer using Cu Kα radiation (λ = 0.154 18 nm), with the X-ray tube operated at 40 kV and 40 mA. The single crystal X-ray diffraction (SXRD) data were performed in Jilin University. The IC analyses were recorded on an 883 Basic IC plus-Metrohm, and the emission spectra on a SHIMADZU RF-5301pc fluorescence spectrophotometer. The ESR results were obtained in the Institute of Chemistry, Chinese Academic of Sciences. Electrochemical measurement was performed on a CHI-660 instrument. Total organic carbon (TOC) measurement was performed on a TOC-L CPN instrument(SHIMADZU).
For the photocatalytic experiments, a Xe lamp (300 W) (from Jingyuan Co. Ltd., Beijing) was used to provide the visible light. To eliminate ultraviolet (UV) light and ensure visible light (λ > 420 nm) irradiation, a cutoff filter (3 cm in diameter) was placed in front of the lamp to completely remove the light of wavelengths less than 420 nm 30 . The light intensity at the sample surface was 38 mW/cm 2 . RhB, MO and glyphosate were selected as pollutants for degradation at room temperature. Prior to illumination, the suspension containing 80 mg of catalyst and 100 mL of dye or glyphosate solution (20 mg L −1 ) was stirred for 30 min in the dark for adsorption-desorption equilibrium. Then 1 mL of H 2 O 2 was added to the suspension and the Xe lamp was turned on for the start of degradation. At given time intervals, 2 mL of suspension was collected with a syringe and treated by needle tube filtration (0.45 μm, PVDF membrane) and analyzed. For dye degradation, the analysis was by means of UV/Vis spectrophotometry whereas for glyphosate degradation, it was by TOC and IC methods.

Synthesis of copper (I) complex.
The reaction was carried out in a 10 mL high pressure resistant glass bottle under autogenous pressure. The reactor with pyrazine-2, 3-dicarboxylic acid (1 mmol, 168 mg), Mg(OH) 2 (1 mmol, 58 mg), copper nitrate trihydrate (0.5 mmol, 121 mg), oxalyl dihydrazide (1 mmol, 118 mg) and H 2 O (5 mL) was sealed and heated at 120 °C for 24 h before cooling to room temperature. The brown cubic crystals were collected by filtration, washed with purified water and ethanol and dried in air at room temperature. The product yield was 67% based on Cu(II): Anal. Calcd In the FT-IR spectra of the complex, a high intensity broad band observed in the range of 3700-3500 cm −1 is attributed to OH stretching of the H 2 O. A medium intensity band in the range of 1625-1600 cm −1 is attributed to CN stretching which shifts lower to 1597-1542 cm −1 after coordination. This is further supported by the appearance of a medium intensity band in the range of 525-520 cm −1 which is assigned to Cu-N stretching 31 . The absence of strong characteristic peaks around 1720 cm −1 indicates that all carboxylate groups are completely deprotonated 32 .
X-ray crystallography. The data were collected with Mo Kα radiation (λ= 0.71073 Å) on a Siemens SMART CCD diffractometer for the copper (I) complex. The structure was solved using direct methods with the SHELXTL program and refined using SHELXL-2016 by full-matrix least-squares techniques, the non-hydrogen atoms were assigned with aniso-tropic displacement parameters in the refinement, while the hydrogen atoms were treated using a riding model. The water H atoms were placed in calculated positions with O-H equal to 0.82 Å, and with torsion angles refined, Uiso (H) = 1.5Ueq(C, O). Aromatic H atoms were placed in calculated positions with C-H equal to 0.93(Å) and refined with Uiso (H) = 1.2Ueq(C). The copper (I) complex has been assigned the deposition number CCDC No. 1949198 and the data can be obtained free of charge from the Cambridge Crystallographic Data Centre via http://www.ccdc.cam.ac.uk/data request/cif. The crystal data, data collection and structure refinement details are summarized in Table 1.

Results and Discussion
Synthesis and structure. The copper (I) complex was in situ synthesized by hydrothermal method. During the reaction, oxalyl dihydrazide decomposed into hydrazine and oxalate upon heating. Then hydrazine reduced copper (II) to cuprous ions while oxalate reacted with Mg 2+ to form colorless magnesium oxalate dehydrate. The cuprous ions coordinated with pyrazine 2,3-dicarboxylate while Mg 2+ participated in coordination as counterbalance ions to form the copper (I) complex. We attempted to obtain the target product by replacing oxalyl dihydrazide with hydrazine hydrate or ascorbic acid, and Mg(OH) 2 with MgCl 2 but failed. It is referred that both oxalyl dihydrazide and Mg(OH) 2 play an important role in the self-assembly process. Furthermore, it was observed that the redox reaction is a slow process and cuprous ion in diluted concentration is beneficial to the growth of single crystals.
The crystal structure of the copper (I) complex is shown in Fig. 1. The complex crystallizes into a monoclinic system with P21/c space group. The central Cu1 ion coordinates with two carboxyl oxygen atoms (O1 and O3) and two nitrogen atoms (N1 and N2) originating from three pzdc 2− ligands, forming a distorted tetrahedron. The two N donors from the same pzdc 2− coordinate with two different Cu + ions from the sides of pyrazine ring, forming a chain that extends into 1D space. The carboxyl group C3O1O2 (O1) coordinates to the Cu1 ion in a monodentate mode. The other carboxyl group C4AO3AO4A coordinates to Cu1A and Mg1A simultaneously (where symmetry code A is 1-X, 1-Y, -Z). The Mg 2+ ion coordinates with the oxygen atoms of five water molecules as well as a carbonyl group oxygen atom from pzdc 2− , forming a distorted octahedral geometry. Also, two Cu + ions and two pzdc 2− form a [Cu 2 (pzdc) 2 ] basic unit with distorted chair ring structure, and such a unit extends into 1D space with the pyrazine rings in parallel arrangement. Each Mg 2+ shares a carbonyl oxygen atom from pzdc 2− and  Table 1. Summary of crystal data, data collection and structure refinement for the complex. www.nature.com/scientificreports www.nature.com/scientificreports/ decorated the diagonal angle of the unit like an antennae. Each pzdc 2− provided five coordination atoms (N2, N3, O1, O3 and O4).
Selected bond lengths, angles and hydrogen bonds are given in Table 2. The Cu-O and Cu-N bond distance ranges from 2.156(2) Å to 2.176(2) Å and from 1.942(2) to 1.978(2), respectively. The data are different from those of reported Cu-O(pzdc 2− ) (1.942 Å, 1.980 Å) and Cu-N(pzdc 2− ) (2.023 Å) distances, with the former obviously longer and the latter a little shorter. As for the N − Cu-O bond angles, they are in the scope of 79.83(9)° to 120.81(9)°. These phenomena can be attributed to the different sizes of the central Cu ions (Cu 2+ (d 9 ) and Cu + (d 10 )) as well as to Jahn-Teller effect.
There are intermolecular hydrogen-bonding interactions (e.g., O-H···O and C-H···O) between crystal water molecules and pzdc 2− , coordination water molecules and pzdc 2− as well as crystal water molecules and coordination water molecules (Fig. 2). The distances range from 2.656(3) to 3.298(4) Å. All the interactions promote the stability of the complex structure.
Electrochemical measurement. Cyclic voltammogram (CV) of the copper (I) complex was recorded at a potential scan rate of 50 mV s −1 in water solutions containing 1 mol L −1 of KOH (Fig. 3). A conventional three-electrode arrangement was adopted, consisting of a glassy carbon as working electrode, saturated calomel as reference electrode, and a Pt wire as counter electrode. The sample was adhered to the working electrode. The CV reveals an incompletely reversible oxidation-reduction process in the "−1 to 0 V" range. Oxidation potential is observed at −0.233 V and reduction potential at −0.733 V and −0.373 V. It is inferred that the CV response is resulted from the following half reactions 33     On the oxidation scan, a single peak is observed, which is assigned to the complex two electrons oxidation half-reaction (Eq. 1). On the reduction scan, two well-defined peaks develop separated by about 360 mV, which show two stepwise reduction processes 36 (Eqs. 2 and 3). The incompletely reversibility of the CV profile indicates that the mixed valence [Cu I Cu II (pzdc) 2 ] + and fully oxidized [Cu II Cu II Mg(pzdc) 2 ] 2+ intermediates maintain their integrity in the time scale of the CV experiment. We conclude that the oxidation of complex is Cu-centered which represents oxidation of Cu + to its Cu 2+ form.
Photophysical properties. The UV/Vis absorption spectra of free ligand 2,3-pyrazinedicarboxylic acid and copper (I) complex in solid form are shown in Fig. 4. The ligand shows intense absorption bands at 256-320 nm, which are assigned to the spin-allowed ligand-centered (LC) π-π* transition. As for the copper (I) complex, the intense absorption bands below 320 nm are also due to spin-allowed LC π-π* transition. In the 328-600 nm region, the copper (I) complex shows a broad shoulder, which can be attributed to metal-to-ligand charge-transfer (MLCT) transitions.
The copper (I) complex exhibits blue photoluminescence emission (Fig. 5), which peaks at 468 nm. The emission is tentatively assigned to MLCT excited state rather than to cluster-centered (CC) triplet emission that consists of a combination of ligand-to-copper charge transfer (XMCT) and copper-centered d → s/p transitions 37 . It is mainly because the shortest Cu···Cu distance in the copper (I) complex is 4.369 Å, which is much larger than the sum of the vander Waals radii of Cu(I) (2.80 Å) [38][39][40] . This may be why the copper (I) complex does not display a remarkable photoluminescent property.  To further evaluate the photocatalytic effect of copper (I) complex, the oxidation of glyphosate was carried out under similar conditions. Because glyphosate does not show any UV-Vis absorption, the degradation of glyphosate was monitored by TOC. There is no glyphosate conversion in the absence of copper (I) complex. In the presence of copper (I) complex, glyphosate was completely mineralized in 40 min (Fig. 7). The results confirm that the copper (I) complex plays an important role in promoting the degradation of RhB, MO and glyphosate. Comparatively speaking, the degradation rate caused by copper (I) complex is faster than that caused by Cu 2 O nanoparticles, P25 or Cu 2 O-RGO-3 nanocomposite 41 , which degrade pollutants over 2 hours under the same conditions. We conclude that the catalytic systems must possess three factors including: oxidant, catalyst, and light. When visible light is introduced to a turbid liquid system containing RhB (MO or glyphosate)/Cu (I)/H 2 O 2 , the degradation rate of pollutants is faster than the reaction undergo without light irradiation, because visible light supplies much higher energy for the reaction. All the results suggest that H 2 O 2 , as oxidant, complex Cu (I), as catalyst, play an important role in the degradation rate of the pollutants, and light energy accelerates the degradation of pollutants.
Considering reusability is an essential factor for the application of a photocatalyst, we tested the recyclability of copper (I) complex in four cycles of glyphosate degradation (Fig. 7). The results show that there is no significant decrease of degradation efficiency across the four runs. Moreover, the PXRD pattern of the used sample is similar to that of the fresh sample (Fig. 7, inset), revealing that the catalyst is photochemically stable during the degradation process.  www.nature.com/scientificreports www.nature.com/scientificreports/ Catalytic mechanism. ESR technique was used to capture short-lived radicals during the degradation process under darkness and visible light irradiation conditions. As shown in Fig. 8, signals of 5,5-dimethyl-1-pyrroline-N-oxide (DMPO)/ • OH adducts are clearly observed in the dark as well as under visible light irradiation, displaying the characteristic intensity ratio of 1:2:2:1(hyperfine coupling constants α H = α N = 14.9 G) 42,43 . With increase of light absorption, there is increase of signal intensity (from 30 to 60 s). Nonetheless, the signal intensity is much smaller in the dark, implying that the degradation rate is slower in the absence of visible light irradiation. In addition, the corresponding inorganic ions (NO 3 − and PO 4 3− ) were detected by ion chromatography. These findings provide direct evidence for the participation of •OH radicals in the photocatalytic processes. It is inferred that the •OH radicals of high oxidation potential facilitate the degradation, and with visible light absorption, the degradation of the dyes and glyphosate is accelerated.
The degradation mechanism is complicated. It is difficult to monitor the decomposed intermediate compounds because of the rapid degradation. Based on the change of •OH radical and TOC content, as well as the information related to N and P products and CV curves, it is inferred that •OH radicals are dominant active species in the photocatalytic processes [44][45][46]    conclusion In summary, a new cuprous polymer with 2,3-pyrazinedicarboxylic acid ligands was synthesized by hydrothermal method. It is noteworthy that the central Cu + ions are in situ redox reaction. The polymer possesses photoluminescence property, exhibiting emission behavior similar to that observed in solid state. In addition, the polymer shows effective catalytic activity in the degradation of dyes and glyphosate under moderate reaction conditions using H 2 O 2 as green oxidant. The polymer can be easily recovered and reused in these heterogeneous catalytic systems without significant loss of catalytic activity. The plausible catalytic mechanism suggests the generation of •OH radicals and active copper intermediates that are responsible for the degradation of the substrates. Based on the outstanding performance of the polymer, it is envisaged that it has high application potentials in the field of catalysis.