Four isostructural lanthanide metal-organic frameworks: Syntheses, structures, and fluorescence sensing of Fe3+ and ciprofloxacin hydrochloride

Hong-Mei CHAI Jia-Ling YAN Xue-Hua SUN Gang-Qiang ZHANG Yi-Xia REN Lou-Jun GAO

Citation:  Hong-Mei CHAI, Jia-Ling YAN, Xue-Hua SUN, Gang-Qiang ZHANG, Yi-Xia REN, Lou-Jun GAO. Four isostructural lanthanide metal-organic frameworks: Syntheses, structures, and fluorescence sensing of Fe3+ and ciprofloxacin hydrochloride[J]. Chinese Journal of Inorganic Chemistry, 2023, 39(4): 775-784. doi: 10.11862/CJIC.2023.039 shu

四种同构镧系金属有机框架的合成、结构和荧光传感Fe3+和盐酸环丙沙星

    通讯作者: 任宜霞, renyixia1@163.com
    高楼军, glj@yau.edu.cn
  • 基金项目:

    国家自然科学基金 22063010

摘要: 采用溶剂热法,以含氮四羧酸3,5-二(3',5'-二羧苯)-1H-1,2,4-三唑(H4BDT)为配体,成功合成了4种同构镧系金属有机框架(Ln-MOFs):{[La3(BDT)2(HCOO)(H2O)5]·0.5H2O·3DMF}n(1)、{[Ce3(BDT)2(HCOO)(H2O)5]·3DMF}n(2)、{[Pr3(BDT)2(HCOO)(H2O)5]·3DMF}n(3)和{[Nd3(BDT)2(HCOO)(H2O)5]·3DMF}n(4),并采用单晶X射线衍射、粉末X射线衍射、元素分析、热重、傅里叶换红外光谱、N2吸附实验和荧光光谱对其进行表征。结果表明,这些Ln-MOFs均为单斜C2/m空间群晶体,是双核为无机建筑单元的三维介孔结构。其中2可选择性荧光检测Fe3+离子和盐酸环丙沙星药物分子,检测限分别为4.59和0.77 μmol·L-1

English

  • In recent decades, with the growth of population, the large‐scale development of human activities such as industry, agriculture, and aquaculture has led to the release of more and more dangerous chemicals, and their potential toxicity and non‐degradability have directly resulted in serious environmental problems[1-2]. In particular, increasingly prominent water pollution poses a huge threat to the ecological environment and human health[3].

    Iron ion is one of the necessary trace elements for the human body. It plays an important role in many physiological and pathological processes such as oxygen transport, hemoglobin formation, cell metabolism, and DNA replication[4]. However, the lack or excess of Fe3+ ions in organisms will lead to liver damage[5], anemia[6], heart disease[7], cancer[8], and other physiological abnormalities. Therefore, effective detection of Fe3+ ions is of great importance for human health.

    Ciprofloxacin hydrochloride (CIP) is a thirdgeneration synthetic fluoroquinolone antibiotic, which is one of the most widely used clinical antibiotics in the world because of its minimal side effects. CIP has potent activity against both Gram‐positive and Gram‐negative bacteria and can treat infections caused by single or multiple resistance of bacteria to other antibiotics[9]. However, more and more studies have shown that CIP can induce DNA damage[10] and may lead to severe liver damage[11] and hematuria[12]. Therefore, the detection of CIP in the water environment is also essential.

    The common detection methods for Fe3+ ion and CIP include the atomic absorption method[13], chromatography[14], mass spectrometry[15], atomic fluorescence[16], etc. But these methods are often cumbersome. Therefore, it is quite necessary to develop or establish analytical techniques and strategies for detecting, monitoring, and removing harmful pollutants in the water environment, which are simple, rapid, and sensitive in operation to reduce the risk of pollution.

    The metal‐organic framework (MOF) is a new type of porous coordination polymer, which is comprised of electron‐donating organic ligands and coupling units (metal ions or metal‐oxygen cluster units) connected by coordination bonds[17]. Due to its characteristics of low toxicity, porosity, large specific surface area, aperture structure, and functional diversity and tunability, it has been widely used in the fields of gas adsorption[18], storage[19], separation[20], heterogeneous catalysis[21], luminescence sensing[22], magnetism[23], biosensing[24], and biomedicine[25]. In particular, the lanthanide metal‐organic frameworks (Ln‐MOFs) material has the luminescence characteristics of π conjugates of organic ligands and lanthanide ions. It has unique advantages in the selective recognition and detection of metal cations and inorganic anions, which have been widely used in environmental science, medicine, life science, and the nuclear industry.

    In this work, different lanthanide metal salts and 3, 5‐bis(3′, 5′‐dicarboxyphenyl)‐1H‐1, 2, 4‐triazole (H4BDT) as a connector were selected to synthesize four isostructural Ln‐MOFs by the solvothermal method: {[La3(BDT)2(HCOO)(H2O)5]·0.5H2O·3DMF}n (1), {[Ce3(BDT)2(HCOO)(H2O)5]·3DMF}n (2), {[Pr3(BDT)2(HCOO)(H2O)5]·3DMF}n (3), and {[Nd3(BDT)2(HCOO)(H2O)5]·3DMF}n (4). And single‐crystal X‐ray diffraction elemental analyses, FT‐IR, powder X‐ray diffraction (PXRD), N2 adsorption, and thermogravimetric analysis (TGA) were employed for characterizing the synthesized products. The fluorescence sensing performance of 2 was further discussed, and it was found that 2 showed special sensing and recognition to Fe3+ and CIP in aqueous solution.

    The reagents used throughout this work were all commercially available and could be directly used in experimental research without any processing. Among them, organic ligands came from Jinan Henghua Technology Co., Ltd. And four lanthanide metal salts were all from Aladdin Co., Ltd. (Shanghai), and the purity was 99%, AR, CP, and 99.9%, respectively.

    Elemental analyses (C, H, and N) were performed using a Vario EL elemental analyzer. The crystallinity of the Ln‐MOFs synthesized particles was determined by PXRD using a Shimadzu XRD‐7000 X‐ray diffractometer with Cu radiation (λ=0.154 06 nm, U=45 kV, I=40 mA, 2θ=5°‐30°). TGA was performed by a TGA5500 model. N2 adsorption isotherm was observed by automatic specific surface and porosity analyzer (MicroActive 4.03). Infrared spectra were recorded by a Shimadzu IRAFFINITY‐1S spectrometer in a range of 4 000-500 cm-1. Fluorescence spectra were recorded by a Hitachi F‐7000 fluorescence spectrophotometer. The UV‐Vis absorption spectrum was recorded by a UV3600PLUS220/230VC type UV‐Vis spectrophotometer of Shimadzu.

    A mixture of lanthanide metal salts (La(NO3)3·6H2O for 1, Ce(NO3)3·6H2O for 2, PrCl3·6H2O for 3, and Nd(NO3)3·6H2O for 4) (0.05 mmol), H4BDT (0.1 mmol), 4, 4′‐bipyridine (0.05 mmol for 2, 0.1 mmol for 1, 3, 4), DMF (1.5 mL for 2, 2 mL for 1, 3, 4), H2O (4 mL for 2, 3 mL for 1, 3, 4), HNO3 (five drops, 10%) was added to a 25 mL Teflon lined stainless steel autoclave. The temperature was gradually increased to 160 ℃ through the operation of the set program and holding 72 h, and then reduced to room temperature at a rate of 3 ℃·h-1. After filtering the synthesized crystals were fully washed with water and ethanol and naturally dried to obtain crystals.

    The colorless rod‐like crystals of 1 were collected (70% yield based on La). Anal. Calcd. for C92H94N18O53La6(%): C, 35.26; H, 3.00; N, 8.05. Found(%): C, 35.20; H, 2.85; N, 7.64. FT‐IR (KBr pellet, cm-1): 3 393(m), 3 054(m), 2 373(w), 2 341(w), 1 640(s), 1 617(s), 1 540(s), 1 114(w), 1 032(w), 926(w), 858(m), 789(s), 757(m), 667(w) (Fig.S1a, Supporting information).

    The colorless rod‐shaped crystals of 2 were collected (65% yield based on Ce). Anal. Calcd. for C46H46N9O26Ce3(%): C, 35.37; H, 2.95; N, 8.07. Found(%): C, 35.39; H, 2.83; N, 7.78. FT‐IR (KBr pellet, cm-1): 3 383(m), 2 343(m), 2 378(m), 1 653(s), 1 636(s), 1 560(s), 1 382(s), 1 116(w), 786(m), 755(m), 684(m), 675(w) (Fig.S1b).

    The green rod‐shaped crystals of 3 were collected (75% yield based on Pr). Anal. Calcd. for C46H46N9O26Pr3(%): C, 35.32; H, 2.94; N, 8.06. Found(%): C, 35.68; H, 2.86; N, 7.96. FT‐IR (KBr pellet, cm-1): 3 432(m), 3 086(m), 2 974(w), 2 347(w), 1 653(s), 1 555(s), 1 433(s), 1 381(s), 1 120(w), 1 026(w), 928(w), 787(s), 755(s), 693(m), 666(w) (Fig.S1c).

    The pink‐purple rod‐like crystals of 4 were collected (75% yield based on Nd). Anal. Calcd. for C46H46N9O26Nd3(%): C, 35.10; H, 2.92; N, 8.01. Found(%): C, 35.14; H, 2.87; N, 7.98. FT‐IR (KBr pellets, cm-1): 3 423(m), 2 378(w), 2 343(w), 1 645(s), 1 636(s), 1 555(s), 1 311(w), 1 124(w), 1 026(w), 928(w), 853(w), 791(m), 755(m), 684(m), 667(w) (Fig.S1d).

    Crystallographic data for Ln‐MOFs were harvested on a Bruker D8 Venture′s single crystal diffractometer at 298 K (Mo radiation, λ=0.071 073 nm), corrected for multi‐scan absorption using SADABS, and the analytical data were adjusted by SHELXL′s full‐matrix minimum square method for F 2. All non‐ hydrogen atoms were optimized with anisotropic displacement parameters. The hydrogen atoms were refined isotropically on calculated positions using a riding model with their Uiso values constrained to 1.2 times the Ueq of their parent atoms. The solvent molecules are highly disordered, which are supposed to form a hydrogen bond with water molecules have been removed by the SQUEEZE routine in the PLATON software package. Crystallographic data and structure refinement details for 1-4 are shown in Table 1. The bond lengths and bond angles of 1-4 are listed in Table S1.

    Table 1

    Table 1.  Crystal data and structure refinement details for 1-4
    下载: 导出CSV
    Parameter 1 2 3 4
    Formula C92H94N18O53La6 C46H46N9O26Ce3 C46H46N9O26Pr3 C46H46N9O26Nd3
    Formula weight 3 131.4 1 560.35 1 562.72 1 572.72
    Crystal system Monoclinic Monoclinic Monoclinic Monoclinic
    Space group C2/m C2/m C2/m C2/m
    a / nm 1.588 0(4) 1.586 2(7) 1.592 5(4) 1.577 7(5)
    b / nm 2.042 6(5) 2.039 9(9) 2.039 2(5) 2.025 9(7)
    c / nm 1.702 7(4) 1.699 3(11) 1.705 5(4) 1.693 4(6)
    β / (°) 110.026(3) 110.142(6) 110.171(3) 110.259(5)
    V / nm3 5.189(2) 5.162(5) 5.199(2) 5.078(3)
    Z 2 4 4 4
    Dc / (g·cm-3) 2.005 2.008 1.997 2.058
    Absorption coefficient / mm-1 2.507 2.682 2.847 3.104
    F(000) 2 596 2 588 2 600 2 612
    θ range for data collection / (°) 2.366-25.019 1.693-28.489 2.579-28.445 2.402-25.018
    Reflection collected 13 193 16 282 16 865 11 724
    Independent reflections (Rint) 4 721 (0.019 4) 6 443 (0.027 1) 6 551 (0.020 1) 4 575 (0.055 3)
    Data, restraint, number of parameters 4 721, 66, 343 6 443, 78, 336 6 551, 78, 336 4 575, 78, 336
    GOF on F 2 0.999 1.031 1.077 1.226
    Final R indices [I > 2σ(I)]* R1=0.036 8, wR2=0.109 0 R1=0.043 9, wR2=0.138 3 R1=0.041 0, wR2=0.120 7 R1=0.067 5, wR2=0.183 4
    R indices (all data) R1=0.041 9, wR2=0.112 9 R1=0.056 1, wR2=0.153 7 R1=0.047 7, wR2=0.125 8 R1=0.088 4, wR2=0.197 0
    $* R_1=\sum\left(\left|F_{\mathrm{o}}\right|-\left|F_{\mathrm{c}}\right|\right) / \sum\left|F_{\mathrm{o}}\right| ; w R_2=\left[\sum w\left(F_{\mathrm{o}}^2-F_{\mathrm{c}}^2\right)^2 / \sum w\left(F_{\mathrm{o}}^2\right)^2\right]^{1 / 2} .$

    The powders of complex 2 (3 mg) were uniformly dispersed in 3 mL of different solutions, treated ultrasonically for a certain period to form a suspension, and stored at room temperature for 3 d for fluorescence measurement. These different solutions included 0.01 mol·L-1 M(NO3)x (Mx+=Zn2+, Ag+, Pb2+, Bi3+, Cd2+, Co2+, Al3+, Hg22+, Ni2+, Fe3+, Cu2+) or drug solutions: amoxicillin (AMX), azithromycin (AZM), trihexyl hydrochloride (TRH), piroxicam (PIX), nitrofurantoin enteric‐coated(NEC), medroxyprogesterone acetate (MA), ribavirin(RBV), chlorpheniramine maleate (CPM), ampicillin(AMP), acetaminophen (ACM), vitamin B1 (VB1), cimetidine (CIM), phenolphthalein (PHPH) metoclopramide (MCPM), CIP.

    The results of X‐ray single crystal diffraction analysis show that Ln‐MOFs 1-4 belong to the monoclinic crystal system with the space group of C2/m (Table 1). Because the four complexes have the same 3D coordination frameworks, the structure of 1 is described herein as a representative.

    The asymmetric unit of complex 1 contains two crystallographically independent La(Ⅲ) ions, one BDT4- anion, one HCOO- anion, and four coordination water molecules (Fig. 1a). La1 lies in a nine‐coordination environment around with seven oxygen atoms (O1, O5, O4a, O7, O8, O3b, and O4b) from five different BDT4- anions, one oxygen atom (O10) from a water molecule, and one oxygen atom (O9) from an HCOO- anion. Among them, O3b and O4b, O7 and O8 are chelated, while O1, O4a, O5, and O9 are in a mono‐dentate bridge coordination position. La2 is centered in an eight‐coordinated pattern of four oxygen atoms (O2, O2c, O6c, and O6) from four different BDT4- anions, four oxygen atoms (O11, O12, O11c, and O13) from four water molecules. The BDT4- anion adopts a highly coordinated fashion: κ1κ1κ1κ1κ1κ2κ1κ1μ7 connecting seven La(Ⅲ) ions (Fig. 1b). Two La1 ions are bridged by the bridging carboxylate oxygen atoms (O4a and O4b), meanwhile, La1 ion is bridged by the bridging carboxylate oxygen atoms (O1 and O5, O2 and O6) with La2 ion, forming a wavy zigzag La2‐La1‐La1‐La2 four‐metal chain (Fig. 2). The adjacent zigzag chains are cross‐peak connected by BDT4- anions to form 2D layers (Fig. 3). The 2D layers are connected by BDT4- anions to form 3D porous structures (Fig. 4a).

    Figure 1

    Figure 1.  (a) Asymmetric unit of complex 1; (b) Coordination environment of the BDT4- ligand

    Symmetry codes: b: -x+1, y, -z+1; c: x, -y+1, z; e: -x+1, y, -z; f: -x+1/2, -y+1/2, -z; g: x-1/2, -y+1/2, z

    Figure 2

    Figure 2.  Coordination diagram of La1, La2, and four metal chain unit

    Symmetry codes: a: x+1/2, -y+1/2, z; b: -x+1, y, -z+1; c: x, -y+1, z; h: 3/2-x, 1/2-y, 1-z; i: 3/2-x, -1/2+y, 1-z

    Figure 3

    Figure 3.  Zigzag chain and 2D layer parallel to ab plane of 1

    Figure 4

    Figure 4.  Three‐dimensional structures of 1-4

    The 3D structures of Ln‐MOFs 2-4 are the same as that of 1 (Fig. 4b‐4d) with the difference in the size of the aperture, which is attributed to the difference in the length of the Ln—O bond and the angle of the O—Ln—O bond. The bond lengths of Ln—O are in a range of 0.237 0(4)‐0.273 8(4) nm (1), 0.234 9(5)‐0.273 7(4) nm (2), 0.234 4(4)‐0.273 9(3) nm (3), and 0.230 6(7)‐0.272 1(7) nm (4), respectively. The scope of O—Ln—O bond angles are in the range of 48.44(11)°‐153.22(19)° (1), 48.80(13)°‐153.4(2)° (2), 49.03(11)°‐153.62(19)° (3), 49.3(2)°‐150.1(3)° (4), respectively. These bond lengths and bond angles conform to the reported ranges of Ln—O bond length and O—Ln—O bond angle[28]. The bond lengths and bond angles of 1-4 are presented in Table S1‐S4, respectively. In 1-4, with the increase of atomic number from 57 (La) to 60 (Nd), the average Ln—O bond lengths decreased from 0.250 7 to 0.245 8 nm gradually due to the lanthanide contraction effect[29].

    PXRD patterns of complexes 1-4 are shown in Fig.S2. The positions of the main peaks in simulated and experimental patterns were consistent with each other, indicating that 1-4 had good phase purity.

    The TGA curves of complexes 1-4 all showed the slow weight loss and fast weight loss processes (Fig.S3). The first slow weight loss occurred before 500 ℃, mainly due to the loss of solvent molecules and coordination water molecules with 21.36% (Calcd. 20.32%) for 1, 20.79% (Calcd. 19.81%) for 2, 20.7% (Calcd. 19.80%) for 3 and 20.58% (Calcd. 19.66%) for 4. The second rapid weight loss occurred in a range of 500-600 ℃, due to the collapse process of the frameworks.

    The N2 adsorption‐desorption isotherms of Ln‐MOFs 1-4 at 77.35 K were measured (Fig.S4), which exhibited the type Ⅱ mode of IUPAC taxon species. The adsorption capacity increased rapidly with the increase of pressure in the low‐pressure stage, while the adsorption capacity increased slowly in the middle‐pressure stage. They also showed an obvious H4‐type hysteresis loop which might be due to capillary condensation[30]. All these results indicate that these complexes are mainly mesoporous structures.

    The Brunauer‐Emmett‐Teller (BET) surface area (SBET), Langmuir surface area (SLangmuir), single point adsorption total pore volume of pores less than 99.406 9 nm width at p/p0=0.98 (VTOT), t‐plot micropore volume (Vmic), Barret‐Joyner‐Halenda (BJH) adsorption average pore width (DBJH), and optimum aperture (Dopt) of the four complexes materials are shown in Table S5, respectively. In particular, t‐plot micropore volumes were almost zero for 1-4, which further indicates that all four complexes are mesoporous structures.

    The fluorescence spectrum results of Ln‐MOFs 1-4 are shown in Fig. 5 (the measured voltage and slit were 600 V and 5.0 nm, respectively). When the excitation wavelength was 256 nm, the characteristic emission peak of 2 was more prominent at 354 nm and the fluorescence intensity was also relatively high. Therefore, the characteristic peak of complex 2 at 354 nm was selected as the detection peak of fluorescence sensing.

    Figure 5

    Figure 5.  Fluorescence intensity of complexes 1-4 in aqueous solution
    2.5.1   Sensing experiments for metal ions

    The luminescence spectra of 2 in different metal cation solutions are shown in Fig. 6a. It was found that the luminescence intensity of 2 was related to the metal cation species. Especially in the Fe3+ ion solution, the luminescence intensity was almost completely quenched. Moreover, by changing the concentration of Fe3+ at a range of 0-300 μmol·L-1 (Fig.S4a), it was found that the luminescence intensity of 2 decreased exponentially with the concentration of Fe3+ ion (Fig. 6b), and the equation was y=1 225.65e-x/11.44+ 3 549.18e-x/482.84-1 599.99 (R2=0.997). Among them, when the concentration was in a range of 0-14 μmol·L-1, there was a good linear relationship between the Fe3+ concentration and the luminescence intensity of 2 (the inset of Fig. 6b): y=69.95x+3 110 (R2=0.996). According to the formula 3σ/k (σ: standard deviation, k: slope), the detection limit was 4.59 μmol·L-1. It indicates that 2 was expected to be used as a new type of luminescent material for Fe3+ ion detection. And the PXRD pattern showed that the structure remained integrated after quenching and recovery (Fig.S2b). It follows that 2 could be served as a stable and recyclable chemical sensing for detecting Fe3+ ions.

    Figure 6

    Figure 6.  (a) Luminescence spectra of complex 2 in different metal cation solutions; (b) Nonlinear and linear (Inset) relationships for identification of Fe3+ by sensor 2

    To understand the fluorescence quenching mechanism, we tested the UV‐Vis absorption spectra of 2 in different metal cation solutions (Fig.S5b). It could be seen that only the Fe3+ solution had an obvious absorption peak at 300 nm, while other metal ions had no obvious absorption peak here. So the quenching of the fluorescence was caused by the energy competition absorption between Fe3+ and organic ligands. At the same time, the detection of fluorescence lifetime was an important means to study the quenching mechanism, so we experimentally determined the fluorescence lifetime of the system before and after complex 2 was quenched by Fe3+ (Fig. 7a). It was found that the fluorescence lifetime before and after quenching was the same. The results indicated that static quenching was the main mechanism of fluorescence quenching of complex 2 after adding Fe3+ [31].

    Figure 7

    Figure 7.  (a) Fluorescence emission decay curves of complex 2 and complex 2+Fe3+ system; (b) Ion‐selective recognition of Fe3+ by 2 in the presence of other metal cations

    The interference of other metal ions on the identification of Fe3+ by sensor 2 is shown in Fig. 7b. 2 shows high selectivity for the identification of Fe3+. So it is affirmed that 2 can be used as a luminescence sensor for detecting Fe3+ in an aqueous solution.

    2.5.2   Sensing experiments for drug molecules

    By recording the fluorescence spectra of 2 in different drug aqueous solutions, we were surprised to find that 2 exhibited amazing luminescence properties in CIP aqueous solution (Fig. 8a). However, the CIP had no other emission peaks except a weak emission peak at 420 nm (Fig. 8b), indicating that its fluorescence did not interfere complex 2.

    Figure 8

    Figure 8.  (a) Fluorescence intensity of 2 in different drug solutions; (b) Comparison of fluorescence spectra of 2 and CIP at room temperature

    The luminescence intensity of 2 increased gradually with the increasing concentration of CIP (Fig. 9a). There was a good linear relationship between the luminescence intensity of 2 and the concentration of CIP when the concentration was in a range of 1-10 μmol·L-1, the linear equation was y=3 374.464+417.285x (R2=0.995), and the detection limit was 0.77 μmol·L-1. The PXRD pattern showed that the structure remained integrated after sensing and recovery (Fig.S2b). It follows that 2 can be used as a stable and recyclable chemical sensing for detecting CIP.

    Figure 9

    Figure 9.  (a) Fluorescence spectra of 2 upon the addition of CIP; (b) Linear relationship for sensing CIP by sensor 2

    The possible mechanism of CIP enhancing the fluorescence of complex 2 was further investigated. Because CIP is a kind of fluoroquinolone antibiotic that possesses β‐diketone moiety composed of its carboxylate and carbonyl, and β‐diketone has the double ketone groups linked with methylene group to produce the chelation with Ce3+, CIP can transfer its absorbed energy to Ce3+ and sensitize the fluorescence of Ce3+, a typical Ce3+ emission can be observed after the coordination of CIP with Ce3+ [9, 32].

    In summary, four isostructural 3D mesoporous Ln‐MOFs based on H4BDT have been successfully synthesized. It is confirmed that they have the same structure, high phase purity, and good thermal stability through various characterizations. The fluorescence performance exhibits that 2 can be used as a diversified fluorescent probe to detect Fe3+ and ciprofloxacin hydrochloride in an aqueous solution with high sensitivity and selectivity. In addition, the mechanism of fluorescence detection of 2 has been preliminarily discussed. The sensing performance of 2 makes it expected to be further developed as an efficient detection material for water pollutants with application value.

    Supporting information is available at http://www.wjhxxb.cn


    Acknowledgments: This work was supported by the National Natural Science Foundation of China (Grant No.22063010). Conflicts of interest: The authors declare no competing financial interest.
    1. [1]

      Zhao L, Song X Z, Wang H, Wang X Y, Wu D, Wei Q, Ju H X. Eu (Ⅱ) MOF as NIR probe for highly efficient instantaneous anodic electroluminescence realized environmental pollutant trace monitoring[J]. Chem. Eng. J., 2022, 446:  136912. doi: 10.1016/j.cej.2022.136912

    2. [2]

      Yang G L, Jiang X L, Xu H, Zhao B. Applications of MOFs as luminescent sensors for environmental pollutants[J]. Small, 2021, 17:  2005327. doi: 10.1002/smll.202005327

    3. [3]

      Qin G X, Wang J, Li L, Yuan F F, Zha Q Q, Bai W B, Ni Y H. Highly water-stable Cd-MOF/Tb3+ ultrathin fluorescence nanosheets for ultrasensitive and selective detection of cefixime[J]. Talanta, 2021, 221:  121421. doi: 10.1016/j.talanta.2020.121421

    4. [4]

      Qi C X, Xu Y B, Li H, Chen X B, Xu L, Liu B. A highly sensitive and selective turn off fluorescence sensor for Fe3+ detection based on a terbium metal organic framework[J]. J. Solid State Chem., 2021, 294:  121835. doi: 10.1016/j.jssc.2020.121835

    5. [5]

      Wu L J, Ding Q, Wang X, Li P, Fan N N, Zhou Y Q, Tong L L, Zhang W, Zhang W, Tang B. Visualization of dynamic changes in labile iron (Ⅱ) pools in endoplasmic reticulum stress-mediated drug-induced liver injury[J]. Anal. Chem., 2020, 92:  1245-1251. doi: 10.1021/acs.analchem.9b04411

    6. [6]

      Dey N, Ali A, Kamra M, Bhattacharya S. Simultaneous sensing of ferritin and apoferritin proteins using an iron-responsive dye and evaluation of physiological parameters associated with serum iron estimation[J]. J. Mater. Chem. B, 2019, 7:  986-993. doi: 10.1039/C8TB01523F

    7. [7]

      Zecca L, Youdim M B H, Riederer P, Connor J R, Crichton R R. Iron, brain ageing and neurodegenerative disorders[J]. Nat. Rev. Neurosci., 2004, 5:  863-873. doi: 10.1038/nrn1537

    8. [8]

      Chen Y Q, Sun X B, Pan W, Yu G F, Wang J P. Fe3+-sensitive carbon dots for detection of Fe3+ in aqueous solution and intracellular imaging of Fe3+ inside fungal cells[J]. Front. Chem., 2019, 7:  911-919.

    9. [9]

      Tan H L, Zhang L, Ma C J, Song Y H, Xu F G, Chen S H, Wang L. Terbium based coordination polymer nanoparticles for detection of ciprofloxacin in tablets and biological fluids[J]. ACS Appl. Mater. Interfaces, 2013, 5:  11791-11796. doi: 10.1021/am403442q

    10. [10]

      Gürbay A, Gonthier B, Signorini-Allibe N, Barret L, Favier A, Hıncal F. Ciprofloxacin-induced DNA damage in primary culture of rat astrocytes and protection by vitamin E[J]. Neurotoxicology, 2006, 27:  6-10. doi: 10.1016/j.neuro.2005.05.007

    11. [11]

      Zimpfer A, Propst A, Mikuz , G , Vogel W, Terracciano L, Stadlmann S. Ciprofloxacin-induced acute liver injury: Case report and review of literature[J]. Virchows Arch., 2004, 444:  87-89. doi: 10.1007/s00428-003-0917-9

    12. [12]

      Garlando F, Täuber M G, Joos B, Oelz O, Lüthy R. Ciprofloxacin induced hematuria[J]. Infection, 1985, 13:  177-178. doi: 10.1007/BF01642807

    13. [13]

      Atsever N, Borahan T, Bakırdere E G, Bakırdere S. Determination of iron in hair samples by slotted quartz tube-flame atomic absorption spectrometry after switchable solvent liquid phase extraction[J]. J. Pharm. Biomed. Anal., 2020, 186:  113274. doi: 10.1016/j.jpba.2020.113274

    14. [14]

      Si T T, Lu X F, Zhang H X, Liang X J, Wang S A, Guo Y. A new strategy for the preparation of core shell MOF/Polymer composite material as the mixed-mode stationary phase for hydrophilic interaction/reversed-phase chromatography[J]. Anal. Chim. Acta, 2021, 1143:  181-188. doi: 10.1016/j.aca.2020.11.053

    15. [15]

      Okabe S, Oda K, Muto M, Sahoo Y V, Tanaka M. Speciation and determination of iron in aqueous solution and river water by high resolution electrospray ionization mass spectrometry[J]. J. Mol. Liq., 2021, 329:  115532. doi: 10.1016/j.molliq.2021.115532

    16. [16]

      Pourjavid, Sehat, Arabieh, Yousefi, Hosseini, Rezaee, M. Column solid phase extraction and flame atomic absorption spectrometric determination of manganese (Ⅱ) and ion (Ⅲ) ions in water, food and biological samples using 3-(1-methyl-1H-pyrrol-2-yl)1H-pyrazole-5-carboxylic acid on synthesized graphene oxide[J]. Mater. Sci. Eng. C-Mater. Biol. Appl., 2014, 35:  370-378. doi: 10.1016/j.msec.2013.11.029

    17. [17]

      Zhang S A, Rong F L, Guo C P, Duan F H, He L H, Wang M H, Zhang Z H, Kang M M, Du M. Metal organic frameworks (MOFs) based electrochemical biosensors for early cancer diagnosis in vitro[J]. Coord. Chem. Rev., 2021, 439:  213948. doi: 10.1016/j.ccr.2021.213948

    18. [18]

      Wu D, Liu J, Jin J, Cheng J G, Wang M, Yang G P, Wang Y Y. New doubly interpenetrated MOF with[Zn4O] clusters and its doped isomorphic MOF: Sensing, dye, and gas adsorption capacity[J]. Cryst. Growth Des., 2019, 19:  6774-6783. doi: 10.1021/acs.cgd.9b01193

    19. [19]

      Daglar H, Gulbalkan H C, Avci G, Aksu G O, Altundal O F, Altintas C, Erucar I, Keskin S. Effect of metal-organic framework (MOF) database selection on the assessment of gas storage and separation potentials of MOFs[J]. Angew. Chem. Int. Ed., 2021, 60:  7828-7837. doi: 10.1002/anie.202015250

    20. [20]

      Hong D H, Shim H S, Ha J, Moon H R. MOF-on-MOF architectures: Applications in separation, catalysis, and sensing[J]. Bull. Korean Chem. Soc., 2021, 42:  956-969. doi: 10.1002/bkcs.12335

    21. [21]

      Guo T L, Mo K L, Zhang N N, Xiao L P C, Liu W L, Wen L L. Embedded homogeneous ultra fine Pd nanoparticles within MOF ultra-thin nanosheets for heterogeneous catalysis[J]. Dalton Trans., 2021, 50:  1774-1779. doi: 10.1039/D0DT03877F

    22. [22]

      Wang G D, Li Y Z, Shi W J, Zhang B, Hou L, Wang Y Y. A robust cluster-based Eu-MOF as multi-functional fluorescence sensor for detection of antibiotics and pesticides in water[J]. Sens. Actuator B Chem., 2021, 331:  129377. doi: 10.1016/j.snb.2020.129377

    23. [23]

      Gao W, Huang H, Zhou A M, Wei H, Liu J P, Zhang X M. Three 3D LnⅢ MOFs based on a nitro functionalized biphenyltricarboxylate ligand: Syntheses, structures, and magnetic properties[J]. CrystEng-Comm, 2020, 22:  267-274. doi: 10.1039/C9CE01245A

    24. [24]

      Lv M Z, Zhou W, Tavakoli H, Bautista C, Xia J F, Wang Z H, Li X J. Aptamer functionalized metal organic frameworks (MOFs) for biosensing[J]. Biosens. Bioelectron., 2021, 176:  112947. doi: 10.1016/j.bios.2020.112947

    25. [25]

      Ahmadi M, Ayyoubzadeh S M, Ghorbani-Bidkorbeh F, Shahhosseini S, Dadashzadeh S, Asadian E, Mosayebnia M, Siavashy S. An investigation of affecting factors on MOF characteristics for biomedical applications: A systematic review[J]. Heliyon, 2021, 7:  e06914. doi: 10.1016/j.heliyon.2021.e06914

    26. [26]

      Guan L L, Jiang Z W, Cui Y J, Yang Y, Yang D R, Qian G D. An MOF based luminescent sensor array for pattern recognition and quantification of metal ions[J]. Adv. Opt. Mater., 2021, 9:  2002180. doi: 10.1002/adom.202002180

    27. [27]

      Safaei S, Wang J, Junk P C. Incorporation of thiazolothiazole fluorophores into a MOF structure: A highly luminescent Zn (Ⅱ) based MOF as a selective and reversible sensor for Cr2O72-and MnO4-anions[J]. J. Solid State Chem., 2021, 294:  121762. doi: 10.1016/j.jssc.2020.121762

    28. [28]

      Gomez G E, Marin R, Neto A N C, Botas A M P, Ovens J, Kitos A A, Bernini M C, Carlos L D, Soler-Illia G J A A, Murugesu M. Tunable energy transfer process in heterometallic MOF materials based on 2, 6-naphthalenedicarboxylate: Solid-state lighting and near-infrared luminescence thermometry[J]. Chem. Mater., 2020, 32:  7458-7468. doi: 10.1021/acs.chemmater.0c02480

    29. [29]

      Wang X R, Huang Z, Du J, Wang X Z, Gu N, Tian X, Li Y, Liu Y Y, Huo J Z, Ding B. Hydrothermal preparation of five rareearth (Re=Dy, Gd, Ho, Pr, and Sm) luminescent cluster based coordination materials: The first MOFs based ratiometric fluorescent sensor for lysine and bifunctional sensing platform for insulin and Al3+[J]. Inorg. Chem., 2018, 57:  12885-12899. doi: 10.1021/acs.inorgchem.8b02123

    30. [30]

      Xue Z M, Jiang J Y, Ma M G, Li M F, Mu T C. Gadolinium-based metalorganic framework as an efficient and heterogeneous catalyst to activate epoxides for cycloaddition of CO2 and alcoholysis[J]. ACS Sustain. Chem. Eng., 2017, 5:  2623-2631.

    31. [31]

      李海红, 刘荔贞, 冯锋. 碳量子点荧光猝灭法检测药物中的异鼠李素[J]. 分析测试学报, 2020,34,(9): 514-519. LI H H, LIU L Z, FENG F. Facile synthesis of fluorescence carbon quantum dots and their application in detection of isorhamnetin in medicines[J]. Journal of Instrumental Analysis, 2020, 34(9):  514-519.

    32. [32]

      Wang B H, Yan B. A turn-on fluorescence probe Eu3+ functionalized Ga-MOF integrated with logic gate operation for detecting ppm-level ciprofloxacin (CIP) in urine[J]. Talanta, 2020, 208:  120438. doi: 10.1016/j.talanta.2019.120438

  • Figure 1  (a) Asymmetric unit of complex 1; (b) Coordination environment of the BDT4- ligand

    Symmetry codes: b: -x+1, y, -z+1; c: x, -y+1, z; e: -x+1, y, -z; f: -x+1/2, -y+1/2, -z; g: x-1/2, -y+1/2, z

    Figure 2  Coordination diagram of La1, La2, and four metal chain unit

    Symmetry codes: a: x+1/2, -y+1/2, z; b: -x+1, y, -z+1; c: x, -y+1, z; h: 3/2-x, 1/2-y, 1-z; i: 3/2-x, -1/2+y, 1-z

    Figure 3  Zigzag chain and 2D layer parallel to ab plane of 1

    Figure 4  Three‐dimensional structures of 1-4

    Figure 5  Fluorescence intensity of complexes 1-4 in aqueous solution

    Figure 6  (a) Luminescence spectra of complex 2 in different metal cation solutions; (b) Nonlinear and linear (Inset) relationships for identification of Fe3+ by sensor 2

    Figure 7  (a) Fluorescence emission decay curves of complex 2 and complex 2+Fe3+ system; (b) Ion‐selective recognition of Fe3+ by 2 in the presence of other metal cations

    Figure 8  (a) Fluorescence intensity of 2 in different drug solutions; (b) Comparison of fluorescence spectra of 2 and CIP at room temperature

    Figure 9  (a) Fluorescence spectra of 2 upon the addition of CIP; (b) Linear relationship for sensing CIP by sensor 2

    Table 1.  Crystal data and structure refinement details for 1-4

    Parameter 1 2 3 4
    Formula C92H94N18O53La6 C46H46N9O26Ce3 C46H46N9O26Pr3 C46H46N9O26Nd3
    Formula weight 3 131.4 1 560.35 1 562.72 1 572.72
    Crystal system Monoclinic Monoclinic Monoclinic Monoclinic
    Space group C2/m C2/m C2/m C2/m
    a / nm 1.588 0(4) 1.586 2(7) 1.592 5(4) 1.577 7(5)
    b / nm 2.042 6(5) 2.039 9(9) 2.039 2(5) 2.025 9(7)
    c / nm 1.702 7(4) 1.699 3(11) 1.705 5(4) 1.693 4(6)
    β / (°) 110.026(3) 110.142(6) 110.171(3) 110.259(5)
    V / nm3 5.189(2) 5.162(5) 5.199(2) 5.078(3)
    Z 2 4 4 4
    Dc / (g·cm-3) 2.005 2.008 1.997 2.058
    Absorption coefficient / mm-1 2.507 2.682 2.847 3.104
    F(000) 2 596 2 588 2 600 2 612
    θ range for data collection / (°) 2.366-25.019 1.693-28.489 2.579-28.445 2.402-25.018
    Reflection collected 13 193 16 282 16 865 11 724
    Independent reflections (Rint) 4 721 (0.019 4) 6 443 (0.027 1) 6 551 (0.020 1) 4 575 (0.055 3)
    Data, restraint, number of parameters 4 721, 66, 343 6 443, 78, 336 6 551, 78, 336 4 575, 78, 336
    GOF on F 2 0.999 1.031 1.077 1.226
    Final R indices [I > 2σ(I)]* R1=0.036 8, wR2=0.109 0 R1=0.043 9, wR2=0.138 3 R1=0.041 0, wR2=0.120 7 R1=0.067 5, wR2=0.183 4
    R indices (all data) R1=0.041 9, wR2=0.112 9 R1=0.056 1, wR2=0.153 7 R1=0.047 7, wR2=0.125 8 R1=0.088 4, wR2=0.197 0
    $* R_1=\sum\left(\left|F_{\mathrm{o}}\right|-\left|F_{\mathrm{c}}\right|\right) / \sum\left|F_{\mathrm{o}}\right| ; w R_2=\left[\sum w\left(F_{\mathrm{o}}^2-F_{\mathrm{c}}^2\right)^2 / \sum w\left(F_{\mathrm{o}}^2\right)^2\right]^{1 / 2} .$
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  • 发布日期:  2023-04-10
  • 收稿日期:  2022-10-17
  • 修回日期:  2023-01-18
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