Two new organic–inorganic hybrid supramolecules {(MAPB)[Ag2(SCN)Br3]} (1) and {(MAPB)2[Ag4I8]CH3CN} (2) have been synthesized with silver iodide, silver thiocyanate and 1,3-bis[(4-aminopyridyl)-N-methylene] benzene dibromide in solution. These compounds have been further characterized by IR spectroscopy, UV-Vis spectroscopy, PXRD, TG and single-crystal X-ray diffraction in the solid state. Compounds 1 and 2 have novel structure and good photocatalytic performance on degradation of organic dyes in waste-water.
With the rapid advancement of the global industrialization process in the 21st century, the problem of environmental pollution has gradually become an important issue affecting human survival and development. The most common water pollutants are dyes, heavy metals, organic pollutants. About 10–20% of the dye is released into the body of water each year during production and using [1]. The dye composition is complex and has the characteristics of non-reducible organisms, anti-oxidation, long-lasting stability and hard to be degraded [2]. The azo dyes have been mentioned as being extremely hazardous since this molecule contains one or more chromophores such as azo groups (-N = N-) and takes up the total dye production [3–6]. In many studies, physical, chemical, or biological methods have been used to treat dyes in wastewater, such as membrane separation, adsorption, coagulation, and microbial treatment [1]. However, these methods have many drawbacks: high operating costs, complicated operation methods, and inability to completely decompose stubborn dye molecules, and the formation of large amounts of sludge can also cause secondary pollution. Therefore, the green, highly efficient dye-degrading technology is one of the current efforts of chemists [7–9].
Photocatalysis is an ideal technology for environmental pollution control and clean energy production. This technology can directly use inexhaustible solar energy to promote the reaction [10–13]. In the photocatalyst reaction step, we found that the core of the photocatalytic process is that the catalyst absorbs light energy and generates new redox active sites [14]. A good photocatalyst generally has the following characteristics: strong visible light absorption ability, excited state has a longer life cycle, better charge separation performance, and better charge flowability. These are actually the reflection of the nature of the photocatalytic process. The photocatalytic degradation of dyes by semiconductor photocatalysts is more attractive than conventional chemical oxidation methods because the semiconductors are inexpensive, non-toxic, and can be reused over a long period of time without degrading their photocatalytic activity. In addition, semiconductor catalysts may be recovered by simple filtration, centrifugation, or may be recycled on a fixed catalytic fluidized bed reactor, and their original catalytic activity may remain. This extends the service life of the catalyst to a certain extent, reduces waste and pollution, and increases the demand for its use [15, 16]. In our studies by the introduction of organic cation templates [17] we created different extended structures of anions and explored their properties. The template we studied was nitrogen-bearing heterocyclic organic cations. If the metal is coordinated with the cation, the stability of the target product can be improved [18, 19]. The role of organic cation templates includes equilibrium charge, structure-directing, cavity-stabilized structural frameworks, kinetics, and chemical interactions. Such template effects are important for the self-assembly of supramolecules.
In this article, one novel multi-hapto N-heterocyclic cations (Scheme 1) with new configuration were designed and synthesized as the organic templating agent, and silver iodide or silver thiocyanate were used for molecular self-assembly to synthesize two novel supermolecular compounds (Scheme 2) with expected photocatalytic properties.
The molecular structure of the title dication.
The molecular structure of compounds 1 and 2.
Experimental section
Materials and methods
The multivalent cation MAPB2 + was prepared as bromides according to the literature, while the other chemicals and solvents were of reagent grade and used as purchased without further purification.
The IR spectra were measured on a Shimazu IR435 spectrometer adopting KBr pellets in the scale of 400–4000 cm-1. Elemental analyses of C, H and N were performed using a Perkin–Elmer 240 elemental analyzer. UV–Vis diffuse reflectance spectra (DRS) were recorded with the aid of a Cary 5000 UV-Vis infrared spectrophotometer. UV-Vis absorption spectra were obtained using a UV-5500 PC spectrophotometer. Thermogravimetric analyses (TGA) were carried out on a model NETZSCHTG209 thermal analyzer in a flowing N2 atmosphere of 20 mL min-1 ata heating rate of 10° min-1in the temperature range of 25–800° using platinum crucibles. Compounds 1 and 2 powder patterns were collected on a Philips X-pert X-ray diffractometer at a scanning rate of 4° min-1 in the 2θ range from 6 to 58.46 (compound 1) and 7.422 to 134.15 (compound 2) with graphite monochromatized Mo-Kα radiation (λ= 0.71073 nm) or Cu-Kα radiation (λ= 1.54184 nm).
Compound of synthesis
Synthesis of {(MAPB)[Ag2(SCN)Br3]} (1)
Compounds 1 and 2 were prepared by evaporation of the solvent at room temperature. A solution of AgSCN 8.3 mg (0.05 mmol) with excess KSCN in water was mixed with a solution of 1,3-bis [(4-aminopyridyl)-N-methylene]benzene dibromide 22.6 mg (0.05 mmol) in water and being filtered, white diamond crystal was obtained after three days with an overall yield of 71%. IR (KBr, cm-1):ν= 3309(m), 3122(m), 2074(s), 1688(s), 1642(s), 1503(s), 1170(w), 849(m), 661(w), 589(w) cm-1; Anal.Calc: H, 2.69; C, 28.17; N, 8.94%. Found: H, 2.54; C, 28.25; N, 8.71%.
Synthesis of {(MAPB)2[Ag4I8]CH3CN} (2)
The procedure was similar to the synthesis of compound 1 except to use AgI instead of AgSCN. The reaction gives yellow block crystals. After the reaction, the product was washed with distilled water and anhydrous ethanol. The yield is 70%. IR (KBr, cm-1):ν= 3409(w), 3282(w), 3074(w), 2218(w), 1642(s), 1503(s), 1449(m), 849(m), 761(m), 489(s) cm-1; Anal. Calc: H, 2.29; C, 22.17; N, 6.01%. Found: H, 2.08; C, 22.01; N, 6.08%.
X-ray crystallography study
The single crystal X-ray diffraction data of compound 1 and compound 2 were recorded at 293K on the Bruker SMART CCD diffractometer with a graphite-monochromated Mo-Kα radiation (λ= 0.71073 nm) or Cu-Kα radiation (λ= 1.54184 nm). The reduction and absorption of data is accomplished using the SADABS package. After absorption correction, use shelxtl-97, OLEX-2 and other packaging for analysis [1]. Table 1 summarizes the crystal structure of supramolecular compounds 1 and 2. Table 2 lists the selected bond lengths and bond angles of the crystal structures of supramolecules 1 and 2. Compound 1, CCDC reference numbers:1848446; Compound 2, CCDC reference numbers:1848448.
Crystal data and structure refinement details for 1–2
Compound
1
2
Empirical formula
C19H20Ag2Br3N5S
C38H43Ag4I8N9
Formula weight
805.93
2072.49
Crystal system
monoclinic
orthorhombic
Space group
C2/c
Cmc21
a/Å
24.660(2)
19.6895(4)
b/Å
12.8283(7)
14.9590(4)
c/Å
15.5185(10)
17.9275(3)
α/°
90
90
β/°
104.995(8)
90
γ/°
90
90
Volume/Å3
4742.0(6)
5280.3(2)
Z
8
4
ρ/g cm3
2.258
2.607
μ/mm–;1
6.812
48.740
F(000)
2656.0
1244.0
Crystal size/mm3
0.16×0.16×0.14
0.2021×0.143×0.0825
T/K
293(2)
293(2)
Independent reflections
5441 [Rint = 0.0324, Rsigma = 0.0510]
2973 [Rint = 0.0380, Rsigma = 0.0477]
Data/restraints/parameters
5441/2/279
2973/1/282
GOF on F2
1.031
1.034
Final R indexes [I> = 2σ (I)]
R1 = 0.0505, wR2 = 0.1035
R1 = 0.0385, wR2 = 0.0990
Final R indexes [all data]
R1 = 0.0901, wR2 = 0.1201
R1 = 0.0402, wR2 = 0.1011
Max/Min eÅ-3
1.33/–0.91
1.65/–1.04
Selected bond lengths and bond angles of compounds 1–2
Bond/angles
Å/°
Bond/angles
Å/°
Bond/angles
Å/°
Compound 1
Ag1-Ag2
3.0781(9)
Ag1-Ag21
3.3532(9)
Ag1-Br1
2.5924(10)
Ag1-Br2
2.7777(9)
Ag1-Br31
2.7214(10)
Ag1-Br3
2.8236(10)
Ag2-Br21
2.7247(10)
Ag2-Br3
2.7889(9)
Ag2-S1
2.5017(18)
Br2-Ag21
2.7247(10)
Br3-Ag11
2.7215(10)
S1-C1
1.621(8)
Ag2-Ag1-Ag21
61.97(2)
Ag21-Br2-Ag2
73.96(3)
Br1-Ag1-Ag21
150.05(3)
Ag11-Br3-Ag1
75.83(3)
Br1-Ag1-Ag2
125.94(3)
Ag11-Br3-Ag2
74.95(2)
Br1-Ag1-Br2
105.31(3)
Ag2-Br3-Ag1
66.52(2)
Br1-Ag1-Br3
110.95(3)
C1-S1-Ag2
99.4(2)
Br1-Ag1-Br31
127.78(3)
N1-C1-S1
179.7(7)
Br2-Ag1-Ag21
51.74(2)
Br2-Ag1-Ag2
56.69(2)
Br2-Ag1-Br
112.85(3)
Br3-Ag1-Ag2
56.20(2)
Br3-Ag1-Ag21
97.08(3)
Br31-Ag1-Ag21
53.44(2)
Br31-Ag1-Ag2
106.18(3)
Br31-Ag1-Br2
100.18(3)
Br31-Ag1-Br3
99.41(3)
Br31-Ag1-Br3
99.41(3)
Ag1 -Ag2-Ag11
63.84(3)
Ag1 -Ag2-Ag21
63.09(2)
Ag21-Ag2-Ag11
54.938(18)
Br2-Ag2-Ag1
56.22(2)
Br2-Ag2-Ag11
99.12(2)
Br21-Ag2-Ag1
107.75(3)
Br21-Ag2-Ag11
53.17(2)
Br21-Ag2-Ag21
53.95(2)
Br2-Ag2-Ag21
52.08(2)
Br21-Ag2-Br2
101.28(3)
Br21-Ag2-Br3
99.82(3)
Br3-Ag2-Ag1
57.28(2)
Br3-Ag2-Ag11
51.61(2)
Br3-Ag2-Ag21
98.549(19)
Br3-Ag2-Br2
113.47(3)
S1-Ag2-Ag11
152.89(5)
S1-Ag2-Ag1
138.17(5)
S1-Ag2-Br2
107.10(5)
S1-Ag2-Br21
113.40(5)
S1-Ag2-Br3
120.15(5)
Ag1-Br2-Ag2
67.09(2)
Ag21-Br2-Ag1
75.09(2)
Compound 2
Ag1-Ag2
3.083(3)
Ag1-Ag31
3.213(2)
Ag1-Ag3
3.213(2)
Ag1-I1
3.041(2)
Ag1-I2
2.746(2)
Ag1-I31
2.8795(13)
Ag1-I3
2.8795(13)
Ag2-I31
2.9336(15)
Ag2-I3
2.9336(15)
Ag2-I4
2.744(3)
Ag2-I5
2.935(3)
Ag3-Ag31
3.173(2)
Ag3-I1
2.8780(17)
Ag3-I3
2.8947(15)
Ag3-I5
2.9787(18)
Ag3-I6
2.7801(15)
I1-Ag31
2.8780(17)
I5-Ag31
2.9786(18)
I3-Ag1-Ag2
58.83(4)
I31-Ag1-Ag2
58.83(4)
I3-Ag1-Ag31
106.91(6)
I31-Ag1-Ag3
106.91(6)
I31-Ag1-Ag31
56.42(3)
I3-Ag1-Ag3
56.42(3)
I3-Ag1-I1
105.73(5)
I31-Ag1-I1
105.73(5)
I3-Ag1-I31
117.44(7)
I3-Ag2-Ag1
57.12(4)
I31-Ag2-Ag1
57.12(4)
I3-Ag2-I31
114.04(8)
I31-Ag2-I5
96.97(5)
I3-Ag2-I5
96.97(5)
I4-Ag2-Ag1
134.42(11)
I4-Ag2-I3
110.56(6)
I4-Ag2-I31
110.56(6)
I4-Ag2-I5
126.95(10)
I5-Ag2-Ag1
98.63(8)
Ag31-Ag3-Ag1
60.41(3)
I1-Ag3-Ag1
59.60(5)
I1-Ag3-Ag31
56.55(3)
I1-Ag3-I3
109.73(5)
I1-Ag3-I5
113.76(5)
I3-Ag3-Ag1
55.97(4)
I3-Ag3-Ag31
107.58(3)
I3-Ag3-I5
96.85(5)
I5-Ag3-Ag1
94.91(5)
I5-Ag3-Ag31
57.82(3)
I6-Ag3-Ag1
151.19(7)
I6-Ag3-Ag31
137.30(3)
I6-Ag3-I1
107.47(5)
Ag2-Ag1-Ag3
71.48(6)
I6-Ag3-I3
115.10(5)
Ag2-Ag1-Ag31
71.48(6)
I6-Ag3-I5
113.80(5)
Ag31-Ag1-Ag3
59.18(6)
Ag3-I1-Ag1
65.69(4)
I1-Ag1-Ag2
116.95(8)
Ag31-I1-Ag1
65.69(4)
I1-Ag1-Ag3
54.72(4)
Ag31-I1-Ag3
66.90(6)
I1-Ag1-Ag31
54.72(4)
Ag1-I3-Ag2
64.05(5)
I2-Ag1-Ag2
148.84(10)
I2-Ag1-Ag31
133.68(7)
Ag2-I5-Ag31
76.94(5)
I2-Ag1-I1
94.20(7)
Ag2-I5-Ag3
76.94(5)
I2-Ag1-I31
114.94(4)
Ag31-I5-Ag3
64.36(5)
I2-Ag1-I3
114.94(4)
Photocatalytic activity test
We choose MB as a contaminant model. Photocatalytic activity is determined by the decomposition rate of methylene blue in visible light. 50 mg of supramolecular compounds 1 and 2 were added to a 100 mL of previously prepared MB solution (concentration 1.0×10-5 mol/L) and stirred in the dark for 30 min to achieve adsorption or desorption equilibrium. Photocatalysis uses a 500 W high pressure xenon lamp as a light source. Then use filter to remove ultraviolet light and irradiate. According to the different catalytic properties of each compound, select the appropriate time interval for sampling [20]. After removing the suspension and centrifuging, the supernatant was taken to measure the UV-Vis spectrum.
Results and discussion
Description of crystal structures
Crystal structure of {(MAPB)[Ag2(SCN)Br3]} (1)
The crystals of supramolecular compound 1 belong to the monoclinic system, space group C2/c, and the unit cell parameters are a/Å = 24.660(2), b/Å = 12.8283(7), c/Å = 15.5185(10), β= 104.9950(8)°. Each silver atom coordinates with a bromine atom and a sulfur atom to form a cubane-like structure. As shown in Fig. 1a, a typical asymmetric cell contains a [Ag2(SCN)Br3]2 - anion and a divalent cation. There exists silver-silver interaction between Ag(1) and Ag(2) with the distance of 3.352(12) Å, which is less than 3.44 Å of the van der Waals radius of silver. Adjacent anions and cations are connected by hydrogen bond N3-H3A⋯Br11 = 2.63(3) Å, N3-H3B⋯S12 = 2.66(4) Å, N5-H5B⋯N13 = 2.33 Å. There are other weak forces between adjacent anions and cations in Mercury software. Figure 1b shows the spatial stacking structure of 1. In the Fig. 1c we can see that the distance between the centers of the pyridine rings of the adjacent two cations is 3.526 Å. And this distance is in the normal range of the face to face stacking [21]. Therefore, we can understand that the cation of supramolecular compound 1 has π–π stacking interaction (Fig. 1d).
(a) Minimal repeat unit of supramolecular compound 1, hydrogen atoms, solvent molecules and water have been omitted for clarity (b) Stacked map looking from the b axis (c) The structural packing diagram of the supramolecular compound 1 in which the dashed red line represents the N3-H3A⋯Br11 hydrogen bond, the blue dashed line represents the N3-H3B⋯S12 hydrogen bond, and the green dotted line represents the N5-H5B⋯N13 hydrogen key (d) π–π stacking of cations (MAPB2 +), Anion ligands have been omitted for clarity.
Crystal structure of {(MAPB)2[Ag4I8]CH3CN} (2)
The single crystal diffraction data show that the crystal 2 of the supramolecular compound belongs to an orthorhombic system, the space group is Cmc21, and the unit cell parameter is a/Å = 19.6895(4), b/Å = 14.9590(4), and c/Å = 17.9275 (3), β= 90°, each silver atom coordinates with the iodine atom, forming a classical cubane-like structure. As shown in Fig. 2a for the minimal repeating unit structure, we can see that each Ag atom coordinates with six iodine (including five μ3-I and one t-I) to form an asymmetry. From the stacking pattern of Fig. 2b, it can be seen that the supramolecular compound 2 have hydrogen bonds. An adjacent anion can form hydrogen bonds with bivalent cations. N-H⋯I hydrogen bond distance is 3.002 or 3.526 Å.
(a) Minimal repeat unit of supramolecular compound 2, hydrogen atoms, solvent molecules and water have been omitted for clarity(b) b direction stacking (c) The structural packing diagram of the supramolecular compound 2 in which the dashed green line represents the N-H⋯I hydrogen bond (d) There are no π–π stacking interactions between pyridine rings.
Our group has studied the flexibility of MABP2 + and the complexity of forming anionic ligands [22]. We can understand that the presence of anions in the form of cubane may be related to the radius of the metal ion in the anion or the position of dibenzyl in the cation template.The π–π stacking method in the literature is different. One is a π–π stacking between adjacent benzene rings, and the other is a π–π stacking between adjacent pyridine rings. So the cation packing may be related to the anion metal ion radius. Therefore, we also need more in-depth exploration. From Fig. 2(c) and Fig. 2d we can also see that the adjacent cations are deposited in different ways. Therefore, anionic ligands also have effects on adjacent cations.
X-ray Diffraction (XRD)
In order to further explore the purity of compounds 1–2 and to provide a reliable guarantee for the follow-up property investigation. X-ray Diffraction of compounds 1–2 was done. As shown in Fig. 3, the experimental PXRD pattern of 1–2 corresponds well to the simulated X-ray diffraction pattern, indicating that the bulk phase material is isomorphous.
(a) PXRD pattern of compound 1 (b) PXRD pattern of compound 2.
Thermogravimetric analysis
To investigate the stability of the synthesized compounds, we performed thermochemical experiments on the synthesized compounds. The TG analysis curve of compound 1–2 is shown in Fig. 4. From Fig. 4, we can see that compound 1 starts to lose weight from 275°C, compound 2 begins to lose weight from 350°C; the greater weight loss of compound 1 happen at 275–350°C, and compound 2 loses at 425–475°C. The biggest reason may be the volatile decomposition of organic cations.The decomposition of compounds 1–2 in the second part may be the decomposition of the cation causing the collapse of the anion structure. Therefore, the stability of compound 1 and compound 2 are relatively good.
Thermogravimetric (TG) plot of Compound 1–2.
Optical band gap
Through the UV-Vis diffuse reflectance spectra of these two compounds, we calculated their corresponding bandgap values (Eg). First, the spectrophotometer was used to obtain the spectrum with the reflectance R as the ordinate and the wavelength λ (nm) as the abscissa. Then, the ordinate is transformed according to the Kubelka–Munk equation: F = (1-R)2/2R, and the abscissa is transformed according to the energy formula E(g) = hc/λ. Finally, for the curves F and E, the energy value corresponding to the intersection of the tangent line and the abscissa of the curve where the slope is the maximum is the band gap value of the compound [23]. As shown in Fig. 4, the bandgap values of the two compounds are: 1.76±0.01 eV, 1.74±0.01 eV, respectively, lower than 3.2 eV of TiO2, indicating that these compounds are potential semiconductor photocatalytic materials. In addition, the compound may be directly irradiated with sunlight, since the maximum photon flux of sunlight is about 1.7 e V [24]. Compounds 1–2 having the aforementioned bandgap values are all potential semiconductor materials and may possess better photocatalytic activity.
Photocatalysis
From the calculation of the bandgap value, we learned that compounds 1–2 are a potential semiconductor material and may have good catalytic properties. We explored the photocatalytic properties of compound 1–2 through the decomposition of organic dyes. We chose organic dye MB as a target pollutant for degradation experiments to investigate the photocatalytic properties of compounds 1 and 2. In the process of photocatalysis, 50 mg of 1 was added to MB (100 mL, 1.0×10-5mol·L-1) aqueous solution separately and magnetically stirred in the dark for about 30 min until equilibrium of the mixture. Then under the irradiation of a 500 W High-pressure mercury lamp, the solution was kept continuously stirring with the aid of a magnetic stirrer. Then, 500 mL high pressure mercury lamp was used to sample 3 mL every 30 mins and centrifuged to measure the UV absorption spectrum (UV absorption spectra at different times are shown in the Fig. (6). The characteristic absorption of MB at about 663 nm (MB) was chosen to monitor the photodegradation process. The percentage of degradation can be calculated using Lambert-Beer’s law; Finally, the data is processed using Origin 8.0 software.
As shown in Figs. 6, the absorption peak of MB decreases obviously along with the increase of the irradiation time.
(a) The band gap value of compound 1 (b) The band gap value of compound 2.
Absorption spectra of the MB solution during the decomposition reaction under UV light irradiation deal with (a) the control experiment without any catalyst (b) compound 1(c) compound 2. (d) Photodegradation ofsolution MB under sunlight irradiation with the use of 1–2 and the control experiment without any catalyst.
As shown in Fig. 6, it can be seen that compounds 1 and 2 have obvious photocatalytic activity. The catalytic effect of compounds 1 and 2 is relatively good. From Fig. 6,we can see that in the blank experiment without any catalyst, the MB degradation rate was only 30% within 150 min. In comparison, MB with Compound 1 had a degradation rate of 80% within 80 minutes, and MB with Compound 2 had a degradation rate of 78% within 120 minutes. Therefore, the photocatalytic activity of compound 1 was better than that of compound 2. The result reveals that compounds 1 and 2 may become potential catalysts in the photodegradation of some organic dyes existing in industrial wastewaters under visible light irradiation.
Conclusions
In summary, two novel compounds were synthesized by solvent evaporation. {(MAPB)[Ag2(SCN)Br3]} and {(MAPB)2[Ag4I8]CH3CN} were synthesized by self-assembly via the bivalent cation MAPB2 + with classical halogenide AgSCN, halogenide AgI. The two compounds were fully IR, PXRD, UV-Vis, TG and so on. There are N3-H3A⋯Br11, N3-H3B⋯S12, N5-H5B⋯N13 hydrogen bond interactions and van der waal’s forces between the organic and inorganic anions in compound 1. By calculating the optical bandgap by UV-Vis, we learned that compound 1 and compound 2 are potential semiconductor materials. Photodegradation experiments show that they can stably photodegrade the organic dye MB under high pressure mercury lamp irradiation. Compounds 1 and 2 show excellent photocatalytic activities for the degradation of MB. So compounds 1 and 2 can become potential catalysts in the photodegradation of some organic dyes existing in industrial wastewaters under visible light irradiation. Further work is underway to expand the structure/nature of the potential applications of functional materials.
Footnotes
Acknowledgments
The research efforts of the Niu group were supported by the National ScienceFoundation of China (No. 21671177) is acknowledged.
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