Design and degradation of permanently porous vitamin c and zinc-based metal-organic framework

Design and degradation of permanently porous vitamin c and zinc-based metal-organic framework

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ABSTRACT Bioapplication is an emerging field of metal-organic frameworks (MOF) utilization, but biocompatible MOFs with permanent porosity are still a rarity in the field. In addition,


biocompatibility of MOF constituents is often overlooked when designing bioMOF systems, intended for drug delivery. Herein, we present the a Zn(II) bioMOF based on vitamin C as an


independent ligand (bioNICS-1) forming a three-dimensional chiral framework with permanent microporosity. Comprehensive study of structure stability in biorelavant media in static and


dynamic conditions demonstrates relatively high structure resistivity, retaining a high degree of its parent specific surface area. Robustness of the 3D framework enables a slow degradation


process, resulting in controllable release of bioactive components, as confirmed by kinetic studies. BioNICS-1 can thus be considered as a suitable candidate for the design of a small drug


molecule delivery system, which was demonstrated by successful loading and release of urea—a model drug for topical application—within and from the MOF pores. SIMILAR CONTENT BEING VIEWED BY


OTHERS APPLICATION OF NOVEL NANOMAGNETIC METAL–ORGANIC FRAMEWORKS AS A CATALYST FOR THE SYNTHESIS OF NEW PYRIDINES AND 1,4-DIHYDROPYRIDINES VIA A COOPERATIVE VINYLOGOUS ANOMERIC BASED


OXIDATION Article Open access 05 March 2021 NICKEL FERRITE NANOPARTICLES DOPED ON HOLLOW CARBON MICROSPHERES AS A NOVEL REUSABLE CATALYST FOR SYNTHESIS OF _N_-SUBSTITUTED PYRROLE DERIVATIVES


Article Open access 05 July 2023 CREATING HIERARCHICAL PORES IN METAL–ORGANIC FRAMEWORKS VIA POSTSYNTHETIC REACTIONS Article 28 October 2022 INTRODUCTION Metal-organic frameworks (MOFs) are


crystalline and generally porous materials consisting of metal ions coordinated to organic molecules, capable of forming 2D and 3D structures with specific structural features. Large pore


volume, high surface-to-volume ratio, the possibility of pore functionalization and the use of active constituents, are properties commonly attributed to these materials. MOFs are already


well established in the various fields of science, such as catalysis, gas storage and separation, sensing or electrochemistry and they are increasingly gaining interest in the biomedicine


applications as well1,2,3,4,5. The compositional variety of these materials allows us to create systems with an agreeable toxicological profile for the use of drug delivery, contrast agents


and theranostics6,7,8,9,10. Such MOFs are, if constructed from at least one biologically active unit, further on referred to as bioMOFs11,12,13. From the perspective of MOF design, Zn(II) is


probably one of the most frequently used cations. Its electronic configuration namely enables a variety of coordination geometries ranging from four- to sixfold polyhedra and thus the


formation of many different secondary building units (SBUs), most commonly found either as discrete clusters or infinite rod-like shapes14,15. However, 3D infinite SBUs forming inorganic


skeletons, which have been observed for Mn-, Ni- or Mg-based MOFs for instance, are to the best of our knowledge not yet known for the Zn-based frameworks16,17,18. From the biological


perspective, Zn(II) is an essential element with recommended daily intake (RDI) value of ~10 mg and a crucial component of a large number of enzymes and transcriptional factors19,20. It has


a significant role in response to oxidative stress, DNA replication and damage repair, as well as immune response, apoptosis, aging and synthesis of proteins, for example, collagen21. Zinc’s


toxicity has also been well studied and oral lethal dose (represented by LD50 value) was determined to be close to 3 g kg−1 of body weight in humans22,23. In contrast to Fe(III) being most


frequently used in the design of bioMOFs, Zn with lower RDI than Fe does not have the tendency to bio-accumulate in the body caused by the lack of active physiological excretion


pathways21,24. Moreover, Zn is regarded as an antioxidant mineral, is redox inactive and as a cation (within RDI values) does not promote the generation of undesirable reactive oxygen


species (ROS)19,21. Its antimicrobial activity is depended on concentration and time of contact. Zinc’s effect is a consequence of (i) direct interaction with the microbial membrane leading


to its destabilization and (ii) interaction with nucleic acids and deactivation of the respiratory system25. Therefore, Zn can present a suitable candidate in constructing bioMOF systems.


When designing a bioMOF by using a desired drug or active molecule as a linker, achieving permanent porosity, although desirable, is not always a priority. This is well exampled in a


non-porous bioMIL-5 where both constituents, azelaic acid and Zn(II) are used for the antibacterial treatment of skin disorders and are released in a controllable manner26. Permanent


porosity, with the pores accessible for hosting molecules after solvent removal, would however offer additional bioapplicative opportunities. The lack of permanent porosity or


inaccessibility of the pores for drug molecules in bioMOF structures, when using small endogenous molecules as ligands, is considered to be the main drawback in their development27. There


are however a few examples of porous bioMOFs with therapeutic linkers worth mentioning—(i) analogue Mg-MOF-74, where olsalazine (prodrug of the anti-inflammatory 5-aminosalicylic acid)28


replaced 2,5-dihydroxybenzene-1,4-dicarboxylate (DBDC) as a linker; (ii) medi-MOF-129, which utilizes curcumin (anti-oxidative, anti-inflammatory, anticancer activity) and (iii) bioMIL-330,


which employs 3′3,5′5-azobenzenetetracarboxylate (antimicrobial) as a linker, however, this framework selectively adsorbs CO2 and NO and is not otherwise considered porous. Besides


pharmaceutically active ingredients, there are different groups of organic bio-molecules with abilities to coordinatively bind with metal cations or SBUs, such as amino acids, nucleobasis,


porphyrins or sugars31,32,33,34,35,36,37,38. Vitamins with natural abundance and a variety of biomedical applications have the ability to bind metals through multiple coordination sites as


well. In spite of the apparent advantages that this group of biomolecules offers, vitamin B3 (niacin/nicotinic acid) is, to the best of our knowledge, the only example used as a ligand in


designing bioMOFs39,40,41. In that manner, vitamin C (_L_-ascorbic acid—ASC) also presents a suitable, biologically active linker. Just as vitamin B3, ASC is also water-soluble and has


anti-inflammatory and antioxidant properties however, their pharmacology is very different. Vitamin C is present in plasma and tissues, and presents an essential cofactor in numerous


enzymatic reactions (biosynthesis of collagen, carnitine, and neuropeptides)42. Together with other vitamins and trace elements such as Zn improves immune functions21. Vitamin C is a weak


sugar acid (pKa1 = 4.25 and pKa2 = 11.79) that forms a monoanion (HA) at pH 4–5 and dianion (A) at pH 11–12. Various materials where metal cations are combined with ascorbic acid are known,


yet they possess molecular or 1D chain-like structures or use ascorbic acid only as a sacrificial agent for sensing applications43,44,45,46,47,48,49,50,51. Therefore, a three-dimensional


bioMOF framework composed of ascorbic acid as an independent ligand was not known up until now. Herein we present Zn-based ascorbate MOF (bioNICS-1; bioMOF material of National Institute of


Chemistry, Slovenia), possessing a unique structure with 3D infinite inorganic building unit inter-connected through ascorbate ligands. BioNICS-1 presents, to the best of our knowledge, the


first example of ascorbate with permanent microporosity, enabling the encapsulation of small drug molecules. Insight into the degradation of Zn-ascorbate structure in biorelavant media shows


great potential for controlled drug release. RESULTS AND DISCUSSION BioNICS-1 crystallizes from solvothermal conditions using only ethanol as a solvent. Ethanol was chosen for the synthesis


as it is technologically safe with a relatively low impact on human health and the environment, and is so considered as a green solvent52,53,54. Furthermore, ethanol acts as a weak ligand


and thus has low tendency to coordinatively participate in the formation of framework structure. Consequently, its removal to activate the MOF framework is typically easier than in the case


of the use of stronger-ligand solvents such as water or dimethylformamide. STRUCTURE PROPERTIES A broader size scale of crystals can be achieved either by using modulator (acetic acid)


resulting in the formation of individual crystallites with the size up to 2 µm (bioNICS-1-aa), or the choice of the heating source (microwave) for the synthesis of nanoparticles


(bioNICS-1-mw) with dimensions up to 50 nm. The details of the synthesis procedures are described in the “Methods” section. The particle size of differently prepared bioNICS-1 products was


comparatively estimated by SEM (Supplementary Fig. 1) and Scherrer calculations (Supplementary Table 1). The results of dynamic light scattering (DLS) measurements were not satisfactory for


proper particle size distribution analysis due to the agglomeration tendencies of the nanocrystals55, which can be explained by the low surface charge deducted by Zeta potential measurements


(Supplementary Fig. 2). Upon stirring the suspension of bioNICS-1 in water media, sedimented material does re-disperse—whether or not these are original agglomerates or newly formed ones


remains unclear. Agglomeration of nanoparticles in liquid media is a common occurrence and could be later addressed with surface modifications to provide either greater surface charge or


steric interference56. The crystal structure of bioNICS-1 was determined by using 3D electron diffraction (3DED) (Supplementary Fig. 3, Supplementary Table 2) and further refined with PXRD


(Supplementary Fig. 4, Supplementary Table 3). For electron diffraction study bioNICS-1-aa was used, whereas all the remaining investigations were performed on bioNICS-1 product synthesized


under conventional conditions followed by the activation described in the Supplementary methodes. Results of PXRD, TGA and N2 isotherms deemed these two materials to be the same


(Supplementary Fig. 5). The crystal structure contains infinite three-dimensional inorganic building unit bridged through the ascorbate moieties, with Zn(II) occurring in three different


coordination environments i.e. octahedral, trigonal prismatic and tetrahedral (Fig. 1c). Such coordination diversity of Zn(II) cation within one framework structure is a rarity among MOFs


and is a consequence of the multi-dentate property of ascorbic acid being fully deprotonated with all four hydroxyl and additional carbonyl O atom participating in coordination with Zn(II)


centres (Supplementary Fig. 6). An additional O atom that shares a common vertex of three ZnO6 octahedra is subjected to _C3_ symmetry (Fig. 1d) and belongs to the independent hydroxyl


group, yielding the overall chemical formula of Zn3(ASC)(OH). The chirality of ascorbic acid results in a chiral framework, as bioNICS-1 crystallizes in the space group _I_213. The


arrangement of Zn(II)-centred polyhedra can be simplified as triangular motifs with tetrahedra on their corners, resulting LCV topology (Fig. 1d)57. Even though the ascorbate ligands are not


part of the topological description, their role in linking of the cations is crucial for the formation of the framework, since the absence of ascorbate does not yield any precipitate nor is


this structure possible to obtain with a different linker. A similar arrangement of inorganic units can be found for example in MIL-77(Ni) structure17, but for Zn-based SBUs this is


unprecedented. A complex system of polyhedral inorganic chains forms two types of intersecting channels with type A running along each unit cell axis and type B running along [111] defined


by eight-membered and six-membered rings, having diameters of 6.5 and 5.5 Å respectively (Fig. 1a, b). The open framework structure of bioNICS-1 was confirmed by N2 sorption isothermal


measurements. Type I isotherm classified by IUPAC indicates permanent microporosity with BET surface area of 553 m2 g−1 (Fig. 2a, Supplementary Figs. 7 and 8) and micropore volume of 0.22 


cm3 g−1. Pore size distribution using NLDFT method shows a bimodal distribution of micropores with the peaks centred at 5.6 and 6.6 Å belonging to B and A channel types respectively, already


described above. BioNICS-1 so represents the first case of vitamin C-based MOF material with proven permanent microporosity. Moreover, the high density of Zn(II) sites within bioNICS-1


structure suggests the acid nature of the MOF framework. Indeed, results of temperature-programmed desorption (TPD) of ammonia shown in Fig. 2b and Supplementary Fig. 9 confirms that


approximately 1/3 of the total Zn(II) cations (2.6 mmol g−1) that builds the structure represent mostly weak acid sites that are potentially accessible for therapeutic gasotransmitters, such


as nitric oxide (NO), hydrogen sulfide (H2S) or carbon monoxide (CO)58. STRUCTURE SOLUBILITY IN AQUEOUS MEDIA Due to the open structure, bioNICS-1 is considered as a potential drug carrier.


In addition, because of the nature of building units, the framework itself can represent a source of bioactive components, which can have, with suitable dosing, a therapeutic effect. The


material was first tested for structure thermal stability (Supplementary Figs. 11 and 12) and solubility in water media (see Supplementary Note 1 for details) in order to investigate the


release of the material’s constituents. To approximate bioNICS-1 behaviour to realistic conditions of human organism-environment, the tests included the influence of three different


parameters: (a) the possible impact of pH. For that purpose, water and saline solutions were adapted to pH values of 3.5, 7.4 and 9.0; (b) the presence of ionic species that are most


commonly present in body fluids. For that purpose, saline (0.9% NaCl) and phosphate buffer solution (PBS), in addition to the demineralized water, were used; and (c) the influence of


environment dynamics on the framework. Therefore, the stability tests were performed in steady state and under stirring. Structural stability of material was studied with PXRD and


BET-specific surface measurements of recovered products in comparison to the untreated material. The rate of released Zn(II) cations within the supernatant was also measured by atomic


absorption spectrometry (AAS) analysis in order to better correlate with the degradation, assuming that the detected concentration of released Zn(II) is directly linked with the rate of


framework degradation. In all cases, the majority of the material remains undissolved in water, saline and PBS solutions after 24 h, with its structural integrity remaining generally


unchanged after treatment. However, diffraction peak broadening and decrease of their heights occur due to the decrease in crystallite size. The additional appearance of Zn-oxalate phase,


which is formed as a consequence of partial degradation of ascorbic to oxalic acid, can be observed as well (Fig. 3a and Supplementary Fig. 12). (a) pH of the media does not have a marginal


effect on the material’s degree of solubility or degradation. The pH values of the supernatant settle at around 6 after 24 h, regardless of the initial pH value, type of media and dynamics.


This is however confirmed to be normal, since ascorbic acid being released into the supernatant acts as an efficient buffer in wide range of pH values59. (b) Evidently, the porosity is


preserved to a large extent (up to 68 %) for the products exposed to demineralized water (Supplementary Figs. 14, 16 and Supplementary Table 4). The decrease of the surface area is most


probably affected by the presence of Zn-oxalate phase within the bulk material. The presence of additional ionic species affects the pore accessibility even further. That is, by inducing the


solubility of the parent MOF due to the increase of the ionic strength, as in the case of saline solution, or by provoking progressive degradation of the MOF framework due to the anion


replacement with the ligand, which can take place in phosphate buffer solution60,61. As expected, the framework degrades to a larger extent in saline solutions, which is consistent with the


trend of BET surface area values and 24 h the degradation rate (release of zinc). Modification of micropores during the degradation tests (Supplementary Fig. 15) follows the same trend as a


decrease in BET specific surface area however; average pore size is not significantly affected by dissolution media. The amount of released Zn(II), however, remains under 10% in all cases


(Fig. 3b and Supplementary Fig. 13). Zinc release in PBS solution at dynamic conditions is comparable to the one where the material was exposed to water. On the other side, bioNICS-1 show


profoundly higher insolubility (below 1%) in PBS when leaving the mixture undisturbed. STEM-EDXS elemental mapping revealed that Zn phosphate-based shell with a thickness of ~10 nm is formed


in such conditions (Fig. 3c) which apparently decelerates subsequent dissolution of the Zn-ascorbate framework. (c) This recrystallization process is apparently more pronounced when the


material is subjected to dynamic as opposed to static conditions. Nevertheless, relatively high stability of bioNICS-1, even in acidic or basic starting conditions, is unusual for Zn-based


MOF systems and can be attributed to the sum of specific structural features such as high connectivity of the pentadentate ascorbic acid molecule to Zn(II) centres, the high dimensionality


of inorganic building units and the rigidity of the framework62. The most pronounced effect of dynamics is observed when stirring is applied in PBS solution where ~5% of Zn(II) is released


from the framework (Fig. 3b and Supplementary Fig. 13) and recrystallization to oxalate is most notable (Fig. 3a), resulting in a decrease of microporosity to about 28 % of the parent value


(Supplementary Figs. 14, 16 and Supplementary Table 4). These results however are reassuring, because they imply that the framework can be readily dissolved in conditions that are (out of


tested ones), most closely related to the body’s environment. Therefore, future encapsulated drugs are going to be released and constituents of bioMOF further metabolized. Additional


information of the degradation process was investigated by the release of organic (ligand) constituents from bioNICS-1 framework by liquid NMR (Supplementary Fig. 17). The released ascorbic


acid in aqueous media (water or saline) in all cases additionally degrades into threonic acid representing a common metabolite of a vitamin C63. However, 13C NMR spectra of the bioNICS-1


degradation in PBS solutions indicate the presence of two additional unknown C4 molecular species, which most probably occur as a result of threonic acid esterification with phosphate


anions. KINETICS AND MECHANISM OF STRUCTURE DEGRADATION In a further attempt to investigate the degradation mechanism of bioNICS-1 under different aqueous conditions, the release kinetics


was studied (Fig. 4a). For demineralized water, saline and phosphate buffer solutions the pH was adjusted to 7.4. Zn(II) concentrations were measured by AAS from liquid solutions sampled


after specified times of stirring, ranging from 5 min to 7 days. The release of Zn(II) shows similar trends for all used media, which cannot be described with any specific kinetic model


established for drug release64,65. The Zn(II) cation release is entirely governed by the framework dissolution rate, rather than diffusion through the inert matrix, as presumed by the afore


mentioned models. In the case of bioNICS-1, the release profile shows two stages. Initial dissolution of the bioNICS-1 framework within the first 6 h appears as a slight burst release of


Zn(II) cations followed by a relatively slow dissolution process in a controllable manner, which follows a concentration-independent zero-order rate profile. The framework dissolution is


most likely inhibited by the formation of insoluble Zn(II)-oxo—based species due to the ligand exchange in the shell domains of the crystallite, which significantly slows down the subsequent


dissolution of the framework (Fig. 4d). The dissolution rate is, as expected, the fastest in saline solutions and slowest in PBS solutions, releasing 18 and 5% of Zn2+ from the bioMOF


framework, respectively. The mechanism was confirmed in the case of bioNICS-1 degradation in PBS solution, representing the most biologically relevant medium. The formation of


phosphate-based nanodomains on the bioNICS-1 crystallites has already been proven by TEM elemental mapping as described earlier in the text. On the other hand, the XRD patterns of the


recovered solids from PBS revealed the gradual formation of additional Zn-oxalate phase, as a result of partial degradation of ascorbic acid to oxalic acid (Fig. 4c). Both phases cannot be


complementarily detected using diffraction and microscopic methods. Zn-phosphate domains are of amorphous nature and therefore not detectable by XRD, on the other hand, Zn-oxalate is not


reliably distinguishable from Zn-ascorbate phase by TEM elemental mapping due to the similar zinc content in both investigated phases. The formation of both types of insoluble domains nicely


coincides with the release kinetic profile. Initial dissolution of bioNICS-1 framework is reflected in slight burst release of Zn(II) cations within the first 6 h of treatment. Afterwards,


the release process stabilizes for the remaining time to PBS exposure in linear progression, due to the formation of phosphate- and oxalate-based phases on the shell domains of the


crystallites. In addition, the relative crystallinity of the bioNICS-1 framework deteriorates simultaneously with the recrystallization process of bioNICS-1 to Zn-oxalate (Fig. 4b, and


Supplementary Fig. 18). It can be concluded that the release of Zn(II) cations is subjected to a controllable manner for most of the treatment time and apparently becomes governed by the


solubility of Zn-oxalate rather than bioNICS-1 itself with increasing time of exposure in the solution. The proposed mechanism can be easily projected to the bioNICS-1 degradation in


demineralized water and saline solution as well. The Zn(II) release rates in such conditions are faster as in the case of treatment in PBS solution where the presence of phosphate-based


shell domains additionally inhibits the dissolution process. DRUG LOADING As the intended application of the material is drug delivery and to prove that small-molecule drugs can be


encapsulated and subsequently released from the microporous framework, bioNICS-1 was loaded with urea which is a model drug for topical application and cosmetic agent9,66,67. Namely, the


size of the pores between 5.5. and 6.5 Å, hydrophilic nature of the framework with accessible acid sites as confirmed by ammonia TPD and suitable structural stability in water media, makes


the bioNICS-1 suitable host for urea loading. Other—small—therapeutic molecules such as hydroxycarbamide, dimethyl fumarate, phosphonomethanoic acid and penicillamine68 could also be loaded


into the pores. Drug loading was done via a simple impregnation method where activated material was dispersed in an ethanol solution of urea for 48 h. The TG/DTG curve of the urea-loaded and


dried material (bioNICS-1@urea) show a weight loss of 11.5% in the temperature region between 100 and 220 °C, which is not observed in the TG curve of the pristine bioNICS-1 (Fig. 5a and


Supplementary Fig. 20). The efficient encapsulation of urea drug within the micropores of bioNICS-1 is also indicated by the significant decrease of BET specific surface area from 553 to 150


 m2/g for the pristine and bioNICS-1@urea materials respectively as deduced from the N2 sorption isotherms (Fig. 5b). The absence of the urea-corresponded peaks in the XRD pattern of loaded


material additionally confirms that the drug is confined within the micropores rather than recrystallized separately or on the surface of the material (Supplementary Fig. 19). The capability


of drug release was demonstrated by the immersion of bioNICS-1@urea in demineralized water for 12 h. The urea drug was identified in the supernatant by liquid 1H NMR analysis (inset in Fig.


 5a and Supplementary Fig. 21). Quantitative evaluation of the NMR spectra showed that 9–10 wt.% of the loaded material corresponds to the released urea. With other words, 80–90% of the


loaded drug is released in an aqueous medium within 12 h, which is triggered by the partial degradation of bioNICS-1 framework as described in details above. CONCLUSION A new MOF containing


bio-compatible Zn(II) cations and ascorbic acid as the main constituents were developed using facile solvothermal synthesis with the use of non-toxic solvent ethanol. The first reported case


of Zn-ascorbate MOF (bioNICS-1) is excelled by several unique structural features—diverse Zn(II) coordination geometry forming an infinite three-dimensional inorganic building unit bridged


through ascorbate ligands, resulting in three-dimensional ascorbate-based framework structure with permanent microporosity and accessible acid metal sites. BioNICS-1 was thoroughly examined


for structural stability and solubility in different aqueous conditions using water, saline and PBS solutions adjusted at pH values from 3.5 to 9 under stirring or static conditions.


Framework rigidity and a high degree of Zn(II) binding via all five hydroxyl-type oxygen atoms provides relatively high structure stability and so enable controllable release of bioactive


components. The highest solubility rate is achieved in saline solutions, where ~9% of the framework’s Zn(II) cations were released and about 40% of its initial porosity was preserved after


24 h of stirring. On the other hand, phosphate ions in PBS solution significantly inhibit the framework dissolution due to the formation of less soluble oxalate and phosphate-based domains


on the surface of crystallites as evidenced by XRD, TEM and NMR analysis. BioNICS-1 solubility is almost pH-independent due to the strong buffering effect of the released ascorbic acid


settling the pH of the media at an approximate value of 6. Kinetic studies showed that regardless of the media type, the framework dissolution undergoes two regimes. A slight burst effect is


observed within the first 6 h, followed by a slow dissolution described in zero-order kinetics, releasing 5 and 18% of Zn2+ from bioNICS-1 in PBS and saline solution respectively, within 7


days. The proposed dissolution of the framework is suppressed by the formation of Zn-oxalate shell domains on the surface of the bioNICS-1 crystallites. The accessibility of the micropores


was confirmed by successful impregnation with model drug—urea and its efficient release triggered by the partial framework degradation in aqueous media. Overall, the slow dissolution and


recrystallization process of bioNICS-1 with a burst effect, which could no dubitably be well managed with suitable shaping, makes the material an exceptional and highly promising candidate


for a controlled small drug delivery system provided by its framework microporosity. METHODS SYNTHETIC APPROACHES BioNICS-1 was prepared using EtOH as a solvent with Zn/ASC ratio of 2:1


using conventional heating. Typically 0.752 g of zinc(II) acetate dehydrate (Sigma Aldrich) and 0.3 g of _L_-ascorbic acid (Sigma Aldrich) was added to 10 ml of ethanol (Sigma Aldrich). The


reaction mixture was heated at 120 °C for 1 day in Teflon-lined Stainless-steel autoclaves. Larger independent crystals for the structural analysis were prepared with the addition of acetic


acid (Alfa Aesar). The optimum EtOH/acetic acid volume ratio was 10:1 (1 ml of acetic acid in 10 ml of ethanol). CHARACTERIZATION METHODS X-ray powder diffraction data of the samples were


collected on a PANalytical X’Pert PRO high-resolution diffractometer with CuKa radiation (_λ_ = 1.5406 Å) in the range from 5 to 60° (2θ) with the step of 0.034° per 100 s using fully opened


100 channel X’Celerator detector. For the purposes of Rietveld refinement of the crystal structure model, the XRD powder data was collected on the same equipment using transmission mode in


the range from 5 to 90° 2θ with the step of 0.016°/300 s. Prior to the measurement, the bioNICS-1 sample was degassed at 150 °C overnight and sealed in glass capillary. Morphological


properties and size estimation of the samples was observed by scanning electron microscopy measurements (SEM) on Zeiss Supra™ 3VP field-emission gun microscope. Elemental analysis was


performed by energy dispersive X-ray analysis with an INCA Energy system attached to the above described microscope and by Perkin Elmer 2400 Series II CHNS analyser. The structure of


bioNICS-1 was solved from 3DED data, collected using a JEOL JEM-2100 LaB6 transmission electron microscope. Details of the structure analysis are provided in the Supplementary Methods


section. The thermal analysis (TG/DTG) was performed on a Q5000 IR thermogravimeter (TA Instruments, Inc.). The measurements were carried out in air flow of 10 ml/min, by heating samples


from 25 to 700 °C at the rate of 10 °C min−1. Temperature-programmed X-ray powder diffraction pattern of samples was recorded also on the PANalyticalX’Pert PRO diffractometer additionally


equipped with a high-temperature sample cell, from room temperature to 500 °C in steps of 50 °C in static air. N2 sorption isotherms measurements were performed on Quantachrome AUTOSORB iQ3.


The specific surface areas were determined by Brunauer–Emmett–Teller (BET) method based on the N2 sorption isotherms measured at 77 K in p/po relative pressure range between 4 × 10−2 and 6 


× 10−3 selected according to Roquerol plots. Before the measurement, samples were activated under vacuum at 150 °C for 15 h. The temperature-programmed desorption (TPD) experiments were


performed using the Micromeritics AutoChem II 2920 apparatus. The sample (120 mg) was positioned inside a U-shaped quartz reactor and pre-treated in a flow Ar at 150 °C for 180 min. After


pre-treatment, the latter was cooled to 50 °C and saturated with 10% NH3 in helium for 30 min. Weakly adsorbed NH3 was removed in a flow of pure He for 60 min. The samples were heated to 800


 °C at 20 °C/min and NH3 desorption was monitored by a mass spectrometer (Pfeiffer Vacuum Thermostar) following the characteristic _m/z_ fragments. Pulses of 0.5 mL 10% NH3 in He (Messer)


were used as an external standard for NH3-TPD signal calibration. STEM-EDXS elemental mapping was performed on a probe Cs-corrected Jeol ARM 200CF Scanning Transmission Electron Microscope


equipped with a Centurio Energy Dispersive X-ray Spectroscopy (EDXS) system with a 100 mm2 SDD detector was used for imaging and acquisition of elemental mappings. THE AQUEOUS STABILITY TEST


250 mg of activated bioNICS-1 was suspended in 25 mL of purified water and saline solution, pH was regulated with HCl and NaOH to reach the values of 3.5; 7.4 and 9.0. The test was done in


parallels; one of them was left undisturbed, the other exposed to dynamic conditions on a circular plane mixer for 24 h. Afterwards the samples were left to settle down before separately


collecting the supernatant and the sediment for further analysis. The filtered sediment was left to dry on air over night and its identity was checked and confirmed with PXRD and N2


isotherms analysis. The same procedure was repeated with phosphate buffer solution at pH 7.4. Supernatants were collected and analysed for the presence of organic compounds by NMR


spectroscopy. 10% D2O was added to 0.5 ml of each sample. The samples were transferred to 5 mm NMR tubes and 1H NMR spectra were recorded on a Bruker Avance Neo 600 MHz NMR spectrometer with


a QCI cryo probe at 25 °C using excitation sculpting to suppress the water signal. In addition, 13C, 1H-13C HSQC and 1H-13C HMBC NMR spectra were recorded on the sample of supernatant after


treatment in phosphate buffer solution under dynamic conditions to obtain more detail about the nature of compounds in the sample. Chemical shifts were referenced externally to the chemical


shift of NaTMSP (δH 0 ppm, δC 0 ppm). ZN(II) RELEASE KINETICS The test was a kinetic modification of the previously described procedure presented by Howarth et al. Briefly, 250 mg of


activated bioNICS-1 was suspended in 25 mL of 3 different media (purified water, saline and phosphate buffer solution), which represented about 5 mg of Zn/1 mL media. Solutions had pH of 7.4


which was regulated with HCl and/or NaOH. Samples of release medium (5 mL) were collected for analysis at set time intervals (1, 2, 4, 6, 12, 24, 48, 72, 96 and 168 h) using a syringe with


a 0.80 µm filter attached, and supplemented with the same volume of fresh media. This way the volume of the release medium stayed constant throughout the test, and _sink_ conditions were


maintained. The concentration of Zn(II) cations within the investigated solutions were determined by PerkinElmer AAnalyst 200 flame atomic absorption spectrometer (AAS). The concentration of


the released Zn(II) was calculated using Eq. 1, where Ct(corr.) is the corrected concentration at the time t, Ct is the apparent concentration at the time t, v is the volume of the sample


taken and V is the total volume of the dissolution medium.


$${{{{{{\rm{C}}}}}}}_{{{{{{\rm{t}}}}}}}({{{{{\rm{corr}}}}}}.)={{{{{{\rm{C}}}}}}}_{{{{{{\rm{t}}}}}}}+\frac{{{{{{\rm{v}}}}}}}{{{{{{\rm{V}}}}}}}\mathop{\sum


}\limits_{0}^{{{{{{\rm{t}}}}}}-1}{{{{{{\rm{C}}}}}}}_{{{{{{\rm{t}}}}}}}$$ (1) FRAMEWORK DEGRADATION KINETICS IN PBS 85 mg of activated bioNICS-1 was suspended in 8,5 mL of PBS pH 7.4 and


immediately exposed to dynamic conditions on a circular plane mixer. At a set time point (5 min, 10 min, 20 min, 40 min, 1 h, 2 h, 4 h, 8 h, 12 h, 24 h, 48 h, 72 h, 96 h) individual samples


were filtered, dried on air over night and sediments identity checked with PXRD. The relative crystallinity of the bioNICS-1 material recovered from PBS solution after different times of


exposure was estimated by comparison of peak intensities corresponding to 011 reflection occurring at 6.0° 2θ. The weight contribution of Zn-oxalate which is formed during the above


mentioned process was calculated from Rietveld quantification analysis using TOPAS Academic V6 software package69. DRUG LOADING AND RELEASE EXPERIMENTS Activated bioNICS-1 (200 mg) was


suspended in EtOH solution of urea (25 mg mL−1) for 48 h under constant stirring. Impregnation was done in two parallels, one at room temperature and one at 40 °C. Both residues were


filtered and washed with EtOH, then dried on air over night before proceeding with further tests. The recovered product was immersed in demineralized water for 12 h. After that the


supernatant was qualitatively and quantitatively evaluated by liquid 1H NMR. DATA AVAILABILITY The data generated during this study are included in the manuscript and the Supplementary


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Institute of Chemistry, Slovenia for performing the temperature-programmed desorption experiments. Financing from the Slovenian Research Agency program (P1-0021) is acknowledged. AUTHOR


INFORMATION AUTHORS AND AFFILIATIONS * National Institute of Chemistry, Hajdrihova 19, 1000, Ljubljana, Slovenia Tia K. Tajnšek, Uroš Javornik, Goran Dražić, Nataša Zabukovec Logar & 


Matjaž Mazaj * Faculty of Inorganic Chemistry and Technology, University of Ljubljana, Večna pot 113, 1000, Ljubljana, Slovenia Tia K. Tajnšek * Stockholm University, Frescativägen 8, 106


91, Stockholm, Sweden Erik Svensson Grape & Tom Willhammar * Ruđer Bošković Institute, Bijenička cesta 54, 1000, Zagreb, Croatia Tatjana Antonić Jelić * University of Nova Gorica,


Vipavska 13, 5000, Nova Gorica, Slovenia Nataša Zabukovec Logar Authors * Tia K. Tajnšek View author publications You can also search for this author inPubMed Google Scholar * Erik Svensson


Grape View author publications You can also search for this author inPubMed Google Scholar * Tom Willhammar View author publications You can also search for this author inPubMed Google


Scholar * Tatjana Antonić Jelić View author publications You can also search for this author inPubMed Google Scholar * Uroš Javornik View author publications You can also search for this


author inPubMed Google Scholar * Goran Dražić View author publications You can also search for this author inPubMed Google Scholar * Nataša Zabukovec Logar View author publications You can


also search for this author inPubMed Google Scholar * Matjaž Mazaj View author publications You can also search for this author inPubMed Google Scholar CONTRIBUTIONS T.K.T. and M.M.


performed the majority of the synthesis and experimental work, N.Z.L. contributed in manuscript writing, E.S.G. and T.W. performed the structure analysis by ED, T.A.J. performed AAS


analysis, U.J. covered NMR measurements, G.D. performed STEM-EDS elemental mapping. All authors have given approval to the final version of the manuscript. CORRESPONDING AUTHOR


Correspondence to Matjaž Mazaj. ETHICS DECLARATIONS COMPETING INTERESTS The authors declare no competing interests. PEER REVIEW PEER REVIEW INFORMATION _Communications Chemistry_ thanks


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ARTICLE Tajnšek, T.K., Svensson Grape, E., Willhammar, T. _et al._ Design and degradation of permanently porous vitamin C and zinc-based metal-organic framework. _Commun Chem_ 5, 24 (2022).


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