Multi-metallic MOF based composites for environmental applications: synergizing metal centers and interactions

Wei Wang a, Bergoi Ibarlucea ab, Chuanhui Huang c, Renhao Dong c, Muhannad Al Aiti *ad, Shirong Huang *a and Gianaurelio Cuniberti *a
aInstitute for Materials Science and Max Bergmann Center for Biomaterials, TUD Dresden University of Technology, Dresden, 01062, Germany. E-mail: muhannad.al_aiti@tu-dresden.de; shirong.huang@tu-dresden.de; gianaurelio.cuniberti@tu-dresden.de
bTECNALIA, Basque Research and Technology Alliance (BRTA), Donostia-San Sebastian, 20009, Spain
cCenter for Advancing Electronics Dresden & Faculty of Chemistry and Food Chemistry, TUD Dresden University of Technology, Mommsenstrasse 4, 01062 Dresden, Germany
dDresden Center for Nanoanalysis, Technische Universität Dresden, 01062 Dresden, Germany

Received 1st April 2024 , Accepted 3rd July 2024

First published on 8th July 2024


Abstract

The escalating threat of environmental issues to both nature and humanity over the past two decades underscores the urgency of addressing environmental pollutants. Metal–organic frameworks (MOFs) have emerged as highly promising materials for tackling these challenges. Since their rise in popularity, extensive research has been conducted on MOFs, spanning from design and synthesis to a wide array of applications, such as environmental remediation, gas storage and separation, catalysis, sensors, biomedical and drug delivery systems, energy storage and conversion, and optoelectronic devices, etc. MOFs possess a multitude of advantageous properties such as large specific surface area, tunable porosity, diverse pore structures, multi-channel design, and molecular sieve capabilities, etc., making them particularly attractive for environmental applications. MOF-based composites inherit the excellent properties of MOFs and also exhibit unique physicochemical properties and structures. The tailoring of central coordinated metal ions in MOFs is critical for their adaptability in environmental applications. Although many reviews on monometallic, bimetallic, and polymetallic MOFs have been published, few reviews focusing on MOF-based composites with monometallic, bimetallic, and multi-metallic centers in the context of environmental pollutant treatment have been reported. This review addresses this gap by providing an in-depth overview of the recent progress in MOF-based composites, emphasizing their applications in hazardous gas sensing, electromagnetic wave absorption (EMWA), and pollutant degradation in both aqueous and atmospheric environments and highlighting the importance of the number and type of metal centers present. Additionally, the various categories of MOFs are summarized. MOF-based composites demonstrate significant promise in addressing environmental challenges, and this review provides a clear and valuable perspective on their potential in environmental applications.


1. Introduction

Environmental issues, including massive emissions of hazardous gases and sewage, harmful electromagnetic wave pollution, as well as water pollution issues have become increasingly severe, with advancing human activity. One of the most effective and reliable solutions for the disposal of environmental pollutants at present is materials technology. In the past decades, various types of nanomaterials have been explored and applied. However, an unsatisfying fact is that new materials are obtained after a long period of exploration, although it is undeniable that they can effectively solve some problems. However, as the problems become more complicated, the material obviously encounters its own bottleneck. This result leads to prolongation of the materials research. Repeatedly, the efficiency of solving problems has been greatly reduced. Therefore, multifunctional, versatile materials attracted a great deal of interests in addressing environmental issues.

The materials in question for detection, absorption and degradation of pollutants in both aqueous and atmospheric environments will provide a platform, where pollutant molecules can be detected and they will interact with each other on the surface activated sites to be further absorbed and degraded. The abundant activated sites originated from a large specific surface area, and extra electrons and holes come from heterogeneous atoms, heterogeneous interfaces and defects. Additionally, the porous structure of the material, good electrical conductivity, magnetic properties and the matching characteristics of the two are critical for dealing with electromagnetic pollution. Among other electromagnetic wave absorbing (EMWA) materials that are still widely applied so far carbonyl iron and graphene may be found. The former shows high magnetic permeability, but the disadvantages such as single loss mechanism, narrow absorption frequency band, and weak absorption performance limit its further value. Moreover, the latter exhibits excellent conductivity characteristics, its poor impedance matching characteristics and high filling degree also limit its application.1,2 TiO2 was first used in photocatalysis to degrade refractory organic pollutants and heavy metal ions,3,4 but TiO2 itself has an extremely low utilization rate of sunlight, that is, it can only absorb and utilize UV which accounts for only 5% of sunlight. It is powerless to nearly 45% of visible light. Until the multifunctional materials with multiple unique advantages emerge, metal organic frameworks (MOFs), as potential multifunctional materials, greatly improve the efficiency of material exploration and shows endless possibilities.

MOFs are a class of crystalline porous coordination polymers consisting of metal ions or clusters and organic ligands. However, in the past, there has been a lack of generally accepted definition of the hybrid assembly of anionic polymers and cationic clusters.5–14 A consensus was reached when the work of Hoskins and Robson on MOFs was reported in 1990, which marks a new beginning in their study.15 Yaghi's group16 synthesized and characterized MOF-5 in a groundbreaking work, in which 1,4-benzenedicarboxylate (BDC) as a ligand and Zn2+ as a metallic ion were used being to date the most investigated MOF material. This work is groundbreaking in terms of MOF. MOFs play an important role and value as a new functional material system in many fields.17–27 Due to their structural assembly, they show unique structural advantages, such as being multi-space, multi-components, multi-morphological and tailorable, which endow MOFs many characteristics, including high specific surface area, open metal site, high porosity and structural diversity. Consequentially, MOF-based composites inherit the excellent properties of MOFs, but also exhibit different physicochemical properties and structures.

Over the last two decades, MOF-based composites have shown continuous popularity in environmental applications (Fig. 1). A substantial body of research on MOF-based composites has yielded promising outcomes in addressing environmental concerns.28–46 MOF-based composites possess promising porosity, pore size, specific surface area, microstructure, redox properties, and polarity to exhibit excellent hazardous gas sensing.47–65 Large specific surface area from MOF-based composites provides rich reaction sites and strong light absorption and utilization rate, leading to remarkable effects in photocatalytic degradation of hazardous gases66–70 and water remediation.71–75 In the meantime, the porous structure derived from organic linkers, the good electrical conductivity, the magnetic properties provided by the magnetic metal from the metal center, and the electromagnetic matching properties that can be tailored, have become the advantages of MOF-based composites in EMWA.18,76–79 So far, there have been various reviews in terms of environmental applications.80–90


image file: d4nh00140k-f1.tif
Fig. 1 Number of published papers of MOF-based composites from 2004 to 2023 for gas sensing (red), EMWA (green), water remediation (blue) and air purification (pink) (Web of science, search keywords: metal organic framework, electromagnetic wave absorption, microwave absorption; gas sensor; water remediation; air purification.).

Bimetallic MOFs and their derivatives with special emphases on their preparation and applications were reported.91,92 These works focused on synthetic strategies, and the development of bimetallic MOFs and their derivatives for a variety of applications, summarizing the findings on the influence of polymetallic ions on MOFs, highlighting the challenges associated with their compatibility, and focusing on the techniques employed for the synthesis and characterization of polymetallic MOFs. Additionally, the review about the state-of-the-art on bimetallic MOFs and derived composites for the main current types of electro- and photoelectroncatalytic applications was reported.93 Uniquely, the review about mixed-metal metal–organic frameworks was reported to focus on synthetic approaches, characterization techniques, computational techniques, catalysis, and gas adsorption and separation applications.94 Furthermore, numerous related reviews have been published, each summarizing the development and various applications of MOF-based materials from diverse perspectives. These reviews are integral to advancing the field.95,96 However, few reviews provide a comprehensive overview in treatment of environmental pollutants: (a) monometallic, bimetallic, and multi-metallic MOF-based composites; (b) focusing on various effects on different central metal types for MOF-based composites; (c) as sensing materials for hazardous gas detection, as absorber deals with EMW pollution, as photocatalysts degrade pollutant molecules both in aqueous and atmospheric environments.

In this review, we aim to comb the recent progress in MOF-based composites characterized by monometallic, bimetallic, and multi-metallic centers, emphasizing their applications in the detection, absorption, and degradation of environmental pollutants. Specifically, the discussion centers on their efficacy in hazardous gases sensing, EMWA, and degradation of pollutants in both aqueous and atmospheric environments, as shown in Scheme 1. Moreover, categories of MOFs are summarized. Finally, this work systematically summarizes the effect of different metal ions centers on the characteristics of MOF-based composites, the relationship between advantages and disadvantages, and the further impact of different applications, current challenges, future opportunities, and directions in the design strategies of MOFs with different metal ions centers in the environmental fields.


image file: d4nh00140k-s1.tif
Scheme 1 Schematic diagram of the applications of mono-, bi- and multi-metallic MOF-based materials in Environmental Applications. Parts of them are reproduced with permission from ref. 22, Copyright (2021) Elsevier B.V.,70 Copyright (2021) Elsevier, Copyright (2018) American Chemical Society.97 Copyright (2023) Wiley-VCH GmbH.

2. MOF-based composites for environmental applications

In recent years, there has been a surge of interest in surrounding MOFs owing to their remarkable array of properties and versatile functionalities. MOFs are composed of two essential components: metal nodes and organic linkers. A comprehensive examination of MOFs underscores the imperative for enhancing their environmental sustainability, necessitating modifications to both metallic and organic constituents. Such enhancements may entail substitution or hybridization of these components, which means that the emergence of MOF-based composites. MOF-based composites inherit the excellent properties of MOFs, but also exhibit different physicochemical properties and structures. The structural diversity inherent in organic linkers endows MOF-based composites with a high degree of tunability, enabling the manifestation of diverse architectures with enhanced performance characteristics. Concurrently, the metal nodes play a pivotal role in applications such as hazardous gas sensing, EMWA, and photocatalysis, by facilitating customizable porous structures, favorable electrical conductivity, and serving as a source of magnetism to effectively attenuate electromagnetic waves. Furthermore, the integration of catalytically active centers within MOF-based composites serves to augment electron transfer rates and catalytic efficiency, thus bolstering their efficacy in environmental protection applications. Consequently, a thorough exploration of strategies for enhancing the environmental compatibility of MOF-based composites, predicated upon varying central metal species, is warranted.

Presently, a myriad of environmental pollutants, both of natural origin and anthropogenic, pervade the atmosphere, infiltrate the soil, and permeate water reservoirs, posing significant risks to human health. The primary objective in mitigating these pollutants lies in their detection at ultra-low concentrations, subsequent efficient absorption, and ultimate degradation. Specifically, this following work focuses on three typical applications: the sensing of hazardous gases, the EMWA, and the degradation of pollutants within aqueous and atmospheric domains.

2.1 Sensing of hazardous gases

The pervasive presence of polluting and hazardous gases emanating from diverse sources poses a constant threat to the well-being of living organisms. These gases include ammonia (NH3), nitrogen dioxide (NO2), nitric oxide (NO), hydrogen sulphide (H2S), sulphur dioxide (SO2), carbon dioxide (CO2), carbon monoxide (CO), and others. Beyond specific concentration thresholds in the environment, these gases are deemed lethal. For instance, an excess of 25 parts per million (ppm) of ammonia in the air can jeopardize human skin, respiratory systems, and overall health.98 In addition, H2S up 5 ppm has a harmful impact on the human respiratory system.97 Concentrations of these gases ranging from 100 to 150 ppm, these gases can lead to a loss of smell. In the range of 200 to 300 ppm, the risk escalates to pulmonary edema. Further, exposure to concentrations between 500 and 700 ppm may result in loss of consciousness, while levels surpassing 700 ppm can swiftly lead to death within minutes.99 Excess NO in air can lead to asthma and cancer.100 Therefore, there is a need for monitoring of these gases by designed highly sensitive gas sensors.
2.1.1 Gas sensing mechanisms. Gas sensors refer to a class of devices that are used to detect the concentration of specific gases in the environment. Gas sensors typically consist of two main components: the sensing material and the transducer. The interaction of the sensing material with the target gas results in dielectric fluctuation, magnetic, optical, thermal, acoustic, colourimetric and/or gravitational properties, which can be converted into detectable signals by the transducer. Specifically, the interactions between the sensing materials and the target can be classified into two types. The first is non-covalent interactions, such as van der Waals forces, hydrogen bonding, coordination and π–π interactions. The second is covalent bonding that arises between the sensing materials and the target. The former tends to be a reversible or partially reversible process, while the latter is an irreversible process of action, but the latter offers high sensitivity and selectivity.85 Different gas sensors work on different principles. Semiconductor gas sensors operate by leveraging the interaction between sensing materials and target gases, inducing changes in the resistance of the semiconductor material. This alteration in resistance allows for the measurement of gas concentration.44,48,97,101,102 Electrochemical sensors, on the other hand, utilize gas-induced redox reactions within an electrochemical cell to generate a current signal, facilitating the detection of gas concentration;103–105 optical sensors represent another category, where gases either absorb or scatter light at specific wavelengths, leading to changes in light intensity. For instance, infrared sensors utilize infrared wavelengths to detect the interaction between light and target gas molecules, providing a means to measure gas concentration.106–109 Additionally, there are alternative sensor types such as acoustic wave sensors and electromagnetic induction sensors.110,111
2.1.2 As sensing materials for hazardous gas sensors. MOF-based composites stand out as an innovative class of crystalline nano-porous materials endowed with customized physical and chemical characteristics. These properties include, but are not limited to, porosity, pore size, specific surface area, microstructure, redox properties, and polarity.49,50,56,59,61,65 MOF-based composites excel in integrating precisely tailored host–guest interactions within their porous scaffolds, making them highly promising candidate materials for gas sensing applications. While MOF materials inherently possess insulating properties owing to the regular arrangement of organic ligands obstructing the conducting path,53–55 post-processing of MOFs results in the formation of materials with characteristics resembling graphene or metal oxide composites. This alteration significantly modifies their conductive properties, showcasing distinct structural features and surface chemistry. Importantly, this post-processing ensures the preservation of the MOFs’ porous structure or may even create additional porosity. Consequently, it generates a substantial number of active sites for interactions between the target gas and MOF-based composites. Defect-like graphite or other doped variants of composites can be obtained from organic linkers, which can lead to large and electron-rich π surfaces that can interact with the target gas through van der Waals forces, charge transfer and π–π interactions. Metal oxides can be derived from metal centers featuring chemisorbed oxygen molecules on their surfaces, enabling interactions with target gases through chemical reactions associated with oxygen. Subsequently, researchers have uncovered a novel category of conductive MOF materials. Furthermore, the controllable introduction of defects, doping and functionalization adds active sites with stronger affinity and specificity to the sensing materials, which plays an invaluable role in enhancing gas selectivity and sensitivity of sensors.

Metal centers play a crucial role within MOF-based composites, attributed to the following points: (1) varied metals incorporated into MOFs result in distinct pore structures and surface properties, influencing their selectivity towards gases. (2) Parts of MOFs (such as, Fe, Co, Ni, Cu and Cr-based) exhibit commendable electrical conductivity. The selection of a specific metal profoundly impacts the electronic conductivity of MOFs, consequently influencing the sensitivity and response time of gas sensors. (3) Metals within MOFs can play a role in the adsorption and catalytic reactions of gases, a factor of significance in gas sensor applications. The selection of a specific metal can finely tune the catalytic activity of the MOF, rendering it suitable for various gas sensing applications. (4) The stability of MOFs is influenced by the choice of metals. The formation of parts of metals with specific organic ligands enhances the stability of the MOF, enabling its utilization under more severe environmental conditions, such as high temperature or high humidity. This not only expands the range of applications but also prolongs the lifetime of the MOF.


2.1.2.1 Monometallic MOF-based composites. Monometallic MOFs are relatively simple to design and synthesize, involving only one type of metal ion, which also tends to mean that they exhibit higher stability in sensor applications. In the work of Liu et al.,48 they prepared monometallic Co-MOF and monometallic Zn-MOF sensors for the accurate detection of the hazardous gas H2S. 500 ppb of H2S gas were detected at around 190 °C and 200 °C, respectively, and the results showed that the response was only 1.2%. Similarly another Co-based MOF, Co-PBA with a BET of only 4.0 m2 g−1, and a Ni-based MOF showed 3.2% and 5.9% response results for 100 ppm H2S gas at 200 °C operation temperature.112 Moreover, Cu-based monometallic MOFs,64 Fe-based MOFs,97 Zn-based MOFs47 and In-based MOFs57 have been investigated to deal with H2S (as shown in Fig. 2a–f). Furthermore, Zn, Cu, Ba and Ni-based monometallic MOFs have been applied to cope with N-containing hazardous gases (NH3, NO2 and NO),47,52,58,60,62,63 and it has been investigated that the sensors can be operated at room temperature to show good responsiveness. For example, CuO NPs and CuO TNFs prepared by Liu et al.60 showed good response to NO2, respectively. Especially, CuO TNFs showed a response result of 391.0% in 500 ppb concentration of NO2. The limit of detection (LOD) was 50 ppb. attributed to its higher BET of 11.47 m2 g−1 compared to CuO NPs (3.64 m2 g−1), which is undoubtedly an attractive highlight for a wide range of applications. In contrast, Zn based MOF exhibited 51.41% response exposed to a concentration of 1 ppm at 200 °C operating temperature (Fig. 2g–i).47 Additionally, Zr and Zn based monometallic MOFs have also been applied to detect CO2 and SO2 hazardous gases.113–115 Although the Fe-based MOF, MIL-88B was tailored to modulate the structure of the MOF by the large pore (lp) phase/narrow pore (np) phase ratio by Gang Xu et al.,97 and the optimized MIL-88B-20% exhibited the best sensing performance among all the reported MOF based H2S-sensing materials (Fig. 2j–l), there are still significant limitations to achieve a breakthrough in the field of gas sensing using monometallic MOFs.
image file: d4nh00140k-f2.tif
Fig. 2 (a)–(c) SEM image, selectivity and illustration of the suggested H2S gas sensing mechanism of Cu MOF sensor. Reproduced with permission from ref. 64, Copyright (2022) the authors. (d)–(f) The schematic formation procedure of In MOF and Co/In MOF (e), transient resistance and gas responses to 2 ppm H2S at different temperatures for In MOF (e) and Co/In MOF (f). Reproduced with permission from ref. 57, Copyright (2023) Elsevier B.V. (g)–(i) Schematic representation (g) and stability performance (h)–(i) of the as-prepared sensors. Reproduced with permission from ref. 47, Copyright (2022) Elsevier B.V. (j)–(l) SEM image (j), selectivity (k) and response (l) of as-prepared Fe-MOF. Reproduced with permission from ref. 97, Copyright (2023) Wiley-VCH GmbH.

2.1.2.2 Bimetallic MOF-based composites. The design and synthesis of bimetallic MOF-based composites clearly demonstrated enhanced sensing performance in terms of improved gas uptake and selectivity as well as more precise modulation of physical properties such as porosity, surface area, etc. This is inextricably linked to the fact that two different metals can act synergistically to enhance the performance of MOFs. In contrast to the results observed with Zn and Co monometallic MOFs, the utilization of ZnO/Co3O4 as sensing materials through Zn/Co bimetallic MOFs, a structure acquired by Zn doping in Co MOF, demonstrated superior sensing performance for H2S gas (Fig. 3a and b). Notably, it exhibited exceptional sensitivity, detecting 10 ppb H2S gas at 120 °C. This heightened performance extended to outstanding selectivity and long-term stability, with a remarkable 95% response retention even after 45 days. The remarkable sensing capabilities of this bimetallic MOF structure are primarily ascribed to regular morphology, abundant oxygen vacancies (52.8%) and high specific surface area (96.5 m2 g−1).48 The introduction of additional metal centers appears to play a crucial role in modifying the microstructure of the MOF, leading to an increase in defects and specific surface area. This, in turn, effectively enhances the efficiency of electrical signal transmission. In a parallel fashion, the strategic design of the Cu/Ni bimetallic MOF has propelled the detection of H2S gas to new heights, notably achieving operability at room temperature. The sensor exhibits a substantial advancement, boasting a response range of 64–98% at a gas concentration of 80 ppm. Furthermore, it demonstrates an impressive sensitivity with a LOD ranging from 19–32 ppb, signifying its potential for highly sensitive gas detection applications.64
image file: d4nh00140k-f3.tif
Fig. 3 (a) SEM images of the prepared all samples; (b) responses of the sensors to 500 ppb H2S at different working temperatures. Reproduced with permission from ref. 48, Copyright (2023) Royal Society of Chemistry (RSC). (c) The concentration-dependent response curves of the sensors based on Co3O4@NiO-2.0@Pt3.0 microcubes towards H2S at 200 °C; SEM images of pure Co-PBA (d), Co3O4@NiO-2.0 microcubes (e), elemental mapping images (f) of Co3O4@NiO-2.0@Pt3.0 microcubes. Reproduced with permission from ref. 112, Copyright (2021) Elsevier B.V. SEM images of W MOF (g), W/Zn MOF (h), and W/Zn/Au MOF samples (i). And the elemental mapping images of W/Zn/Au MOF sample (j). The relationship of the operating temperature and response to 10 ppm H2S (k), the long-term stability (l) of samples. The responses to simulated H2S abnormal breath samples and healthy breath samples of W/Zn/Au MOF sample (m). Reproduced with permission from ref. 116, Copyright (2020) Elsevier B.V.

Tan et al.117 synthesized a CoNi bimetallic MOF, from which they derived distinctive double-shelled Co3O4/NiCo2O4 nanocages designed for H2S gas detection. The engineered nanocages exhibited a notable surface-to-volume ratio and a high surface area of 103 m2 g−1. The results demonstrated both high selectivity and a robust gas response, particularly evident in the detection of 100 ppm H2S at the optimal temperature of 250 °C. This underscores the promising potential of the CoNi bimetallic MOF-derived nanocages for effective and sensitive H2S gas sensing applications. Although Hussain et al.118 obtained Cu/Zn bimetallic MOF sensors operating at 250 °C instead of room temperature, the response at lower gas concentrations is very high compared to the corresponding monometallic MOFs sensors64,119 with 425%, while having a ppb level of sensitivity with LOD of 500 ppb. A parallel enhancement in performance is evident in NO2 gas sensing, as demonstrated by Li et al.,120 who employed In/Zn bimetallic MOF sensors. These sensors exhibited remarkably low LOD with results as impressive as 0.2 ppb, coupled with a substantial 185.8% response when exposed to a 1 ppm concentration of NO2 gas. In comparison to the performance of Zn monometallic MOFs,47 this significant improvement can be attributed to the unique molecular characteristics of In, with a diameter of 9.9 Å. Remarkably, this diameter aligns with the cavity size (11.6 Å) and pore size (3.4 Å) of ZIF-8. Consequently, the In atoms can be in situ trapped within the cavities of Zn MOF. The intrinsic gas permeability of the resulting hollow structure, coupled with the electronic sensitization of In metals, collectively contribute to the observed enhancement in gas sensing performance. Furthermore, bimetallic MOF sensors have found application in detecting various hazardous gases, including H2.65


2.1.2.3 Multi-metallic MOF-based composites. Multi-metallic MOFs have higher structural tunability and can be powerful in gas sensing applications by selecting multiple metal ions to achieve more complex properties and enhanced metal synergies. Wang et al. improved the H2S sensing performance of monometallic Co-PBA by introducing Ni metal based on their previous work,112 but the effect is undeniably limited. Further additional introduction of Pt metal improved the response to H2S gas by several tens of times (Fig. 3c–f). Yang et al.116 synthesized Zn based MOF derived WO3/ZnO@Au composites and employed them for H2S gas sensing (Fig. 3g–m). The results showed that Zn/Au/W multi-metallic MOFs composites perform an outstanding gas sensing with 175% response to 10 ppm H2S. The LOD of the sensor is 50 ppb level, and it still exhibits 8.5% response to such a low concentration of H2S. Furthermore, the selectivity and long-term stability of Zn MOFs were validated through experimental confirmation. Notably, the incorporation of multi-heterojunctions and small-sized gold nanoparticles (NPs) efficiently encapsulated within the channels of Zn MOFs plays a crucial role in enhancing the overall sensing performance. The presence of Au or Zn atoms induces electron localization, bringing s-orbital electrons closer to O atoms. This process facilitates their combination into p-orbitals, leading to an increased negative charge on the O atoms and, consequently, enhanced absorption of H2S gas. The introduction of small-sized Au nanoparticles serves a dual purpose: firstly, it augments surface oxygen deficiency through the “spillover effect,” and secondly, it effectively enhances the electrical conductivity of the MOF-derived 3DIO WO3/ZnO@Au sensor. This dual mechanism not only improves gas absorption but also ensures superior electrical properties, collectively contributing to the heightened sensitivity and overall performance of the sensor.

A brief overview of sensing performance of mono-metallic, bi-metallic, and multi-metallic MOFs and its derivatives is reported in Table 1. It includes sensing materials, target gas, sensor condition, LOD, and response. The research work on the use of mono-metallic MOFs for the sensing of hazardous gases is widespread and promising. However, employing only one type of metal may result in relatively low selectivity, limiting the material's capability to discern and detect specific gases.

Table 1 MOF-based composites with mono-, bi- and multi-metallic centers for hazardous gases sensing
Categories Center metals Sensing materials Target gas Sensor condition (°C) LOD (ppm) Response (%/ppm) Ref.
Mono- Zn ZIF-8 CO2 RT 3130 0.7 mLn min−1 115
4.85 774
MOF-5-NH2 SO2 RT 0.05 114
ZIF-8/ZnO nanorod H2S RT 0.05 52/10 119
ZIF-8–500 NO2 200 0.1 51.41/1 47
Cu Cu3(HHTP)(THQ) NH3 RT 0.2 ∼15/100 52
Cu-MOF/PVA/IL H2S RT 1 99/100 64
CuO tube-like nanofibers NO2 RT 0.05 391/0.5 60
CuO NPs 12.5/0.5
SiO2CuOF-graphene-PAni NH3 RT 0.6 63
Ni NiPc-MOF NiNPc-MOF NH3 RT 0.31 ∼50/40 58
H2S 0.02 100/40
NO 0.001 700/40
Y Fum-fcu-MOF H2S RT 0.1 13/10 51
Fe MIL-88B-20% H2S RT 0.17 1061/100 97
In In2O3 H2S 225 2 2.04 57
Ba Ba-MOF NH3 30 1 243/25 62
Zr UiO-66-NH2 SO2 RT 0.005 88.73/50 113
Bi- Zn/Pd ZnO/Pd H2 200 8.5/50 65
Zn/In In/ZnO-10 NO2 300 0.0002 24.6/0.1 120
185.8/1
Cu/Zn CuO/ZnO H2S 250 0.5 425/50 118
Cu/In CuO/In2O3 H2S 70 0.2 229.3/5 121
Cu/Ni NiPc-Cu H2S RT 0.019–0.032 64–98/80 58
Co/Ni Co3O4/NiCo2O4 H2S 250 30 ∼8/100
Co/In In2O3:Co–M H2S 225 0.1 175.5/50 57
Co/Pd SWCNT/PdO-Co3O4 HNCs NO2 100 1 44.11/20 122
Pt/Zn Pt/ZnO-1 wt% 3DIO NPs H2S 320 0.025 11.2/1 123
In/Mo In2O3/MoS2 NO2 RT 0.0088 209/50 124
Ag/Zr (Ag2O@UiO-66IJZr)-NO2 H2S RT 1 90/100 125
Multi- Co/Ni/Pt Co3O4@NiO-2.0@Pt3.0 H2S 200 250/100 112
Zn/Au/W WO3/ZnO@Au H2S 170 0.05 175/10 116


The metal ions within monometallic MOFs establish robust interactions with specific gas molecules, enhancing selectivity towards target gases. For instance, Cu-based MOFs demonstrate high sensitivity to NH3, while Zn-based MOFs exhibit strong adsorption capacities for CO2. The homogeneous distribution of monometallic centers within MOFs ensures consistent active sites, thereby promoting sensor repeatability and reliability. Tailoring MOFs with different monometallic ions allow for flexible adjustment of their physical and chemical properties to meet diverse gas sensing requirements. For example, Fe- and Ni-based MOFs are utilized for detecting oxygen and hydrogen, respectively.

Many monometallic MOFs possess excellent structural stability and maintain consistent sensing performance across a broad range of temperature and humidity conditions. However, their high selectivity can sometimes pose limitations by exhibiting strong responsiveness to specific gases while showing weaker responses to others, which restricts their applicability in complex gas environments. The incorporation of additional metal ions into MOFs evidently enhances their performance in sensing hazardous gases. Bimetallic MOFs harness the synergistic benefits of two distinct metal ions, enabling enhanced interactions with a diverse array of gas molecules. This synergy significantly boosts both selectivity and sensitivity towards specific gases. For instance, a combination such as Pt and Cu can offer high selectivity for gases, like CO and NH3. The incorporation of bimetallic centers within MOFs provides multiple active sites, thereby broadening their applicability across a wide spectrum of gas detection needs. This versatility makes bimetallic MOFs particularly advantageous for use in complex gas environments. However, it is essential to acknowledge that certain bimetallic MOFs may face challenges related to structural instability arising from mismatches between the incorporated metals. This instability can impact the long-term stability of the materials, influencing their practical applications.

The synthesis of bi-metallic MOFs can be relatively intricate, demanding precise control over synthesis conditions. This complexity may, in turn, result in higher production costs. While bi-metallic MOFs offer enhanced performance through synergistic interactions between two metal ions, there are instances where these interactions may lead to interference, affecting overall MOF performance. For example, specific gas molecules may preferentially bind to one metal ion, potentially diminishing the activity of the other metal ion within the MOF structure. Although bimetallic centers generally improve structural stability, certain combinations may still encounter stability challenges under extreme conditions, impacting the long-term durability and reliability of the sensor. Therefore, careful consideration and optimization of bimetallic combinations are crucial to mitigate these potential issues and ensure consistent sensor performance over extended periods.

While we found out that there are many studies on the design and synthesis of multi-metallic MOFs,126–139 they are very limited in hazardous gases sensing applications, which may be due to several reasons as the following: the synthesis of multi-metallic MOFs is usually more difficult than that of monometallic and bimetallic MOFs, which is mainly considered for the stability of multi-metallic MOFs, especially in high temperature or high humidity environments for gas sensing, the structural damage or inactivation of the active sites of multi-metallic MOFs will limit their sensor applications; more importantly, no study has yet been able to demonstrate that the polymetallic MOFs exhibit obvious advantages in terms of hazardous gas sensing compared to mono- and bimetallic MOFs. In consequence, easier to synthesize and structurally stable mono- and bimetallic MOFs are highly favored in the field of hazardous gas sensors.

In the context of hazardous gas sensing applications, the composition of metal ions within MOFs plays a pivotal role. The nature and quantity of these metal ions significantly influence the sensor's efficacy in detecting various hazardous gas molecules, each characterized by distinct structural and chemical properties. Consequently, it becomes imperative to carefully choose metal centers that are amenable to modification by additional metals, fostering synergistic effects. It is crucial to note that the selection of metal centers directly impacts the sensing performance of the MOF. Therefore, a judicious approach should be taken when introducing additional metal centers, aiming to achieve optimal synergies without compromising the sensor's effectiveness. In practice, efforts should be directed towards avoiding excessive introduction of extra metal centers, focusing instead on precision to ensure a substantial enhancement in sensing capabilities.

2.2 Electromagnetic wave absorbing

2.2.1 Electromagnetic pollution. Electromagnetic pollution arises from both natural and man-made sources. Natural electromagnetic pollution is typically caused by natural phenomena, such as lightning, which can result in direct damage to equipment and objects. In severe cases, lighting can generate electromagnetic interference over a broad area in the frequency range of several thousand Hz to several hundred MHz. Natural electromagnetic pollution poses a significant challenge to shortwave communications, as it can cause severe interference. While natural electromagnetic pollution is limited in its occurrence and scope, the rapid advancements in technology have led to widespread and continuous exposure to anthropogenic electromagnetic pollution. Modern technologies such as smartphones, tablets, electric cars, power converters, and navigation systems, communication networks, and electricity transmission systems emit electromagnetic radiation that exposes people to various frequencies of electromagnetic interference on a daily basis.140–143 Anthropogenic sources of electromagnetic pollution are more extensive, stronger, more harmful, and longer-lasting than natural sources.
2.2.2 Electromagnetic waves absorption.
2.2.2.1 Monometallic MOF-based composites. Metals such as Fe, Co and Ni are commonly used as metal centers for MOF materials due to their excellent magnetic and electronic properties. A classical Co-based MOF material (ZIF-67) was successfully prepared by Qin Kuang's group using 2-methylimidazole as organic linkers. The morphological structure obtained (shown in Fig. 4a and b) exhibited a wrinkled surface after annealing treatment, but the dodecahedral structure remained almost unchanged. The material showed excellent EMWA performance with a reflection loss (RL) of −35.3 dB and a thickness of 2.5 mm. The effective absorption bandwidth (EAB) (RL ≤ −10 dB) was 5.80 GHz (8.40–14.20 GHz).78 The excellent EMWA performance is attributed to the synergetic effects among magnetic Co metals, the highly porous structure, and the electrical conductivity of carbon materials. However, the magnetic loss was limited due to the conversion of the surface of the strongly magnetic Co particles to CoO during exposed to air. To address this issue, Yujie Chen and Hua Li developed a monometallic Co source with 2,5-dihydroxyterephthalic acid as organic linkers to obtain another Co-based MOF 74 (shown in Fig. 4c).77 The study showed that the absorbing properties of the material improved to some extent, with an RL of −62.12 dB, a thickness of 2.4 mm and an EAB of 4.6 GHz. This improvement was attributed to the ferromagnetism of the cobalt cores and dielectric properties of the carbon shell. The magnetic properties of the samples were comparable to those of the other studies. However, when the authors replaced the Co source with a Ni source to obtain a monometallic Ni-MOF 74, the material exhibited very limited EMW absorption properties. In our previous research,18 we attempted to enhance the impedance matching of ZIF67 based on cobalt by loading it into rGO, but the results were not as expected. We found that the performance could be improved by incorporating new metal components. While the Co-based MOF modified with carbon nanotubes did not exhibit excellent wave absorption properties (as shown in Fig. 4d–f).144 This may be due to the relatively low or high complex permittivity, or the relatively complex permeability, which leads to poor impedance matching and limits the EMWA performance. However, research on Co-based monometallic MOFs are ongoing due to strongly magnetic nature of cobalt.79,145–149
image file: d4nh00140k-f4.tif
Fig. 4 (a) and (b) High-magnification SEM images of Co-MOF (ZIF-67) precursors, and low-magnification SEM of Co/C-600. Reproduced with permission from ref. 78, Copyright (2015) American Chemical Society. (c) Schematic illustration of porous core–shell Co–C samples. HAADF image, and elemental mapping of Co–C-800. Reproduced with permission from ref. 77, Copyright (2018) American Chemical Society. (d)–(f) SEM images and HRTEM images of the core–shell Co@CNTs-1 composite. RL values of Co@CNTs-1. Reproduced with permission from ref. 144, Copyright (2021) Elsevier Inc. (g)–(i) SEM images of S500. Schematic illustration of porous carbon-wrapped Ni composites. frequency dependence of microwave absorption performance of S500 with different thickness. Reproduced with permission from ref. 150, Copyright (2016) Elsevier B.V. (j)–(l) TEM images of Ni/C-20, calculated delta maps and reflection loss curves of Ni/C-20. Reproduced with permission from ref. 151, Copyright (2019) Elsevier B.V. (m) and (n) TEM images and elemental mapping of C and Ni of NCGF-4. Schematic illustration on microwave absorption mechanism of NCGF. Reproduced with permission from ref. 22, Copyright (2021) Elsevier B.V.

Ni and Co are commonly used as metal centers in MOF materials due to their similar chemical properties. Guangbin Ji's group synthesized Ni-MOFs and utilized the more positive reduction potential of Ni2+ ions (−0.25 V) compared to Co2+ ions (−0.28 V) to obtain carbon-coated Ni metals, while preserving the MOF structure (refer to Fig. 4g–i).150 which exhibits excellent absorption performance with an RL value of −51.8 dB and an EAB of 3.48 GHz for a thickness of 2.6 mm. Dielectric loss resulted from conductivity losses among conductive Ni@C nanospheres, as well as multiple reflection induced by porous structure. Magnetic loss originated from planes of cubic Ni (FCC) instead of hexagonal Ni (HCP), influenced by the content of non-magnetic carbon and the particle size. Compared to Co-MOF, the Ni-MOF synthesized in this study demonstrated poor magnetic properties. Yanhong Zou's group obtained Ni@C composites that exhibit excellent EMWA performance, with an RL of −55.7 dB and an EAB of 6.4 GHz with a thickness of 1.85 mm.152 It is believed that natural loss, rather than the eddy current effect, is responsible for the magnetic loss observed in this composite. Haibo Yang's group synthesized hollow Ni/C microsphere derived from Ni-MOF (refer to Fig. 4j–l),151 which demonstrated remarkable performance with an RL of −57.25 dB with thickness of only 1.8 mm and an EAB of 5.1 GHz. This superior performance is attributed to the hollow structure and the synergistic effect between carbon and nickel nanoparticles. The results highlight the crucial role of Ni particles in magnetic loss mechanism, leading to better impedance matching performance. Our group attempted to improve the electrical conductivity and impedance matching properties of Ni microsphere-like MOFs by implanting them into a graphene foam framework.22 This was achieved by optimizing the GO framework, as illustrated in Fig. 4m and n. The results show that the desired improvement was obtained, with an RL of −63 dB at a loading of only 15 wt%, a thickness of just 1.76 mm, and an EAB of 5.4 GHz. The magnetic properties of the composite were further enhanced by increasing the Ni content in the graphene foam, albeit at the cost of attenuating some of its capability to improve impedance matching. Additionally, many monometallic Ni applications are available in pure MOFs and composites.153–158

Metallic iron and ferrite have been used in EMWA to focus on magnetic loss, thanks to their superior chemical stability and high saturation magnetization strength. However, pure Fe materials have limited electromagnetic wave absorption capabilities, and dielectric loss materials are often in combination with Fe-based materials to achieve impedance matching and boost EMWA performance. A classical Fe based MOF is Prussian blue, which can be heat-treated to produce Fe/C nanocubes (as illustrated in Fig. 5a and b). These nanocubes exhibit ultrawide band EMWA performance with an EAB of 7.2 GHz (range from 10.8 to 18.0 GHz), but their RL falls short of expectations. In addition to the magnetic loss contributed by Fe, the graphitized carbon provides dielectric loss, and multiple dielectric resonances are believed to improve EMWA performance. The natural ferromagnetic resonance is considered the main mode of magnetic loss, and there is no hysteresis loss, domain wall resonance loss, or eddy current effect.159 Further, in addition to Fe particles, Fe3C/Fe and Fe3C/Fe/C composites were derived from other Fe-based MOFs, such as MIL-101.160 Although the EMWA performance generally results in an RL of −39.43 dB, an effective absorption bandwidth of 14.32 GHz (ranging from 3.68 to 18.00 GHz) is mentioned in the literature. It should be noted that another relevant way to evaluate practical applications is to determine the effective absorption bandwidth at a particular thickness, which in this study is approximately 6 GHz with a thickness of 2 mm. Recently, similar research has yielded Fe/Fe3C@NC composites from Fe-MOFs, which exhibit strong RL of −70.8 dB at a thickness of 2.5 mm and an EAB of 5.15 GHz at a matching thickness of 1.7 mm.161 Notably, novel Fe/Fe3O4/FeN/NC composites were obtained from Fe-MOFs (as shown in Fig. 5c and d), exhibiting exceptional EMWA performance, with an RL of −60.08 dB at thickness of merely 1.44 mm and an EAB of 5.06 GHz at 1.64 mm, surpassing many similar researches. This is attributed to the multiple scattering and reflection, interfacial polarization, dipole polarization contributing to dielectric loss, eddy current effects and multiple resonance effects contributing to magnetic loss.162 For monometallic Fe-based MOF materials with strong magnetic properties, achieving good impedance matching and maximizing magnetic loss without excessive loss of dielectric loss both are crucial, and the discovery of complementary materials and content control are indispensable.163–168


image file: d4nh00140k-f5.tif
Fig. 5 (a) and (b) SEM images of the as-prepared PB nanocubes, the reflection losses curves of S2, reproduced with permission from ref. 159, Copyright (2015) Royal Society of Chemistry. (c) and (d) The illustration of formation process of FON/NC@PPy composites, SEM images of Fe-MOF, FON/NC, Elemental mappings of FON/NC@PPy composites, reproduced with permission from ref. 162, Copyright (2021) Elsevier Inc. (e) and (f) SEM micrographs of Mn-MOF-74, MnO@NPC-800 and MnO2@NPC-800 sample, schematics of the MA mechanisms of the MnO@NPC and MnO2@NPC composite materials, reproduced with permission from ref. 169, Copyright (2020) Elsevier B.V. (g) and (h) The FE-SEM images of ZrO2/C-800, three-dimensional RL representations and two-dimensional RL projection maps of ZrO2/C-800, reproduced with permission from ref. 170, Copyright (2020) Royal Society of Chemistry.

In addition to the commonly used magnetic metals, such as Fe, Co, and Ni, other metal centers, including Zn, Zr, Cu, Mn, and Ti, have also been utilized in MOFs materials to achieve efficient EMWA performance. Mn-MOF was employed as a precursor to derive MnO2@C composites by Chongbo Liu's group, resulting in ultra-strong EMWA performance with maximum RL in S, C, X, Ku bands exceeding −50 dB, as shown in Fig. 5e and f.169 The MnO@NPC-800 composite exhibited a RL of is −54.38 dB at 5.12 GHz, demonstrating its superior low-frequency characteristics. Moreover, the MnO2@NPC-800 composites show a maximum RL value −63.21 dB at 12.48 GHz with a thickness of 2.05 mm. It is noteworthy that the composites exhibited good impedance matching with stable and high permittivity and polarization, and relaxation from the 3D caterpillar-like structure, resulting in good reflection loss value in all bands (S, C, X, Ku bands).

The ZrO2/C octahedra derived from Zr-based MOFs (UiO-66) prepared by Jiurong Liu's group focus on EMWA with an RL −58.7 dB at a frequency of 16.8 GHz and a thickness of 1.5 mm. Additionally, the maximum EAB of 5.5 GHz was achieved at a thickness of 1.7 mm (as shown in Fig. 5g and h).170 The results indicate that the dielectric losses are mainly attributed to the derived carbon material, and the degree of carbonization, which depends on the annealing temperature (ZrO2/C-700, 800, 900), determines the material's attenuation capability and impedance matching properties. Proper carbonization leads to excellent EMWA performance.

Zn-based MOFs have also been extensively studied for EMWA. For instance, ZIF-8 MOFs have been employed to prepare ZnO/NC nanocomplexes with two different structures, namely yolk–shell and hollow structures, as depicted in Fig. 6a and b.171 These nanocomplexes exhibited EMWA with different RL value of −51.2 dB and −52.4 dB, respectively, depending on the heat treatment temperature, and an EAB over 4 GHz. The absorption mechanism of these nanocomplexes was attributed to the multiple reflections caused by the hollow structure and the polarization loss of the defect as a center. However, due to the lack of magnetic metal centers, the magnetic component of the electromagnetic wave was not effectively absorbed. Similarly, a core–shell structured ZnO/C@PPy composite was also obtained from ZIF-8 (Zn-based MOF) with a RL of −76.31 dB and an EAB of 6.38 GHz, covering the whole Ku-band, as shown in Fig. 6c–f.172 Nonetheless, this is also shown by the lack of attention to the magnetic component and the problem of impedance mismatch, despite the fact that some wave absorption performance was achieved.


image file: d4nh00140k-f6.tif
Fig. 6 (a) and (b) Schematic routes of synthesis of yolk–shell ZIF-8 and hollow ZIF-8 structures, TEM images of YS-ZnO/NC-800 and H-ZnO/NC-700, reproduced with permission from ref. 171, Copyright (2022) Elsevier Ltd. (c)–(f) Scheme for the synthesis of ZnOC@PPy, the SEM and TEM of Z700@P4, RL of Z700@P4, reproduced with permission from ref. 172, Copyright (2022) Elsevier B.V. (g) Schematic diagram of the synthesis process of CuO@NPC, reproduced with permission from ref. 173, Copyright (2016) The Royal Society of Chemistry.

Guangbin Ji's group synthesized CuO/C composites using the ZIF-67 MOF as a template (shown in Fig. 6g), which exhibit high impedance matching properties, a rarity for non-magnetic monometallics used in EMWA applications. Impedance matching depends on both dielectric and magnetic permeability properties. The obtained CuO/C composites demonstrated an RL −57.5 dB at 14.9 GHz with a thickness of 1.55 mm, and an EAB of 4.7 GHz (13–17.7 GHz) due to the porous carbon material derived from the MOF and high impedance match obtained with Cu embedded in the MOF.173 Additionally, Jun Chen's group synthesized hollow copper-based sulfides with various morphologies, derived from Cu-based MOF (Cu-MOF-74).174 These hollow copper-based sulfides demonstrated low reflection losses, with an RL of only −15 dB, and an EAB of 6.2 GHz at a fill of 20%. The absorption properties are attributed to the synergistic effect of multiple reflections and scattering from the hollow cavity structure, and the conductivity loss from the 3D conductive network. However, the magnetic loss component is lacking and may lead to poor impedance matching, resulting in a smaller RL.

The novel TiO2/C composite has been synthesized, using Ti-based MOF (MIL-125 (Ti)) and exhibited excellent EMWA performance with a minimum RL of −49.6 dB and an effective EAB of 4.6 GHz (13.4–18 GHz) with thickness of 1.6 mm. The EMWA performance is strongly influenced by dielectric losses, including relaxation scheme losses.175 Ti is a space metal known for its light weight, high strength, chemical stability and good corrosion resistance. Although Ti-based MOFs can meet the light weight requirements for wave absorbers, it is important to note that the results of current studies do not demonstrate the potential of monometallic Ti-based MOFs EMW absorption. Relying solely on dielectric losses would be unwise, but combination of magnetic and dielectric-based MOFs could potentially overcome the limitations of a lack of magnetism and make it the best option in the EMWA field.


2.2.2.2 Bimetallic MOF-based composites. Bimetallic MOFs can be divided into two categories: monometallic MOFs lacking magnetic dielectric properties and combined with magnetic dielectric metals (such as Fe, Co and Ni), and MOFs consisting of two strong magnetic metals with strong dielectric properties that complement each other, leading to better impedance matching. Generally, bimetallic MOFs exhibit better EMWA performance than monometallic MOFs. Our research suggests that metals such as Cr, Mn, and Cd, which do not perform well as metal centers alone in MOF materials, can be combined with Co, Fe, or Ni bimetals in MOFs to achieve strong EMWA performance.

As previously mentioned, monometallic Co@C composites have exhibited poor EMWA performance. However, Yang's group was able to improve the performance of Co@C composites by synthesizing Co–Cd- and Co–Zn-based bimetallic-MOFs. Monometallic Co-based MOFs exhibit good magnetic permeability, but weak conductivity leads to an imbalance in impedance matching. To address this issue, Cd and Zn were used to increase the surface area of the material, enhancing the interfacial polarization loss and the multiple reflections, thus contributing to EMWA performance.144 Moreover, the Zn-based MOF has lower dielectric properties, which reduces permittivity to achieve better impedance matching. Renchao Che's group has also synthesized Co@NC–ZnO composites based on Co–Zn-MOF, which demonstrated the strongest RL value of −69.6 dB at only 1.9 mm thickness, with wideband absorption covering 6.8 GHz at 2.4 mm (as shown in Fig. 7). The authors have controlled the Co/Zn mass ratio and adjusted the MOF framework to make the electronic conduction network and magnetic coupling network compatible each other. The unique magnetic coupling and boosted magnetic responding ability were verified using the off-axis electronic holography.176


image file: d4nh00140k-f7.tif
Fig. 7 (a) Morphology evolution, (b–e) TEM images, and (f–i) the reflection loss curves of Co@NC-ZnO-1, Co@NC-ZnO-2, Co@NC-ZnO-3, and Co@NC-ZnO-4, (j) the magnetic coupling, (k) magnetic response unit, and (l) magnetic response scale. Reproduced with permission from ref. 176, Copyright (2021) Wiley-VCH GmbH.

The CoAl-LDH nanoarray was obtained by liquid metal synthesis method using Co-based MOF as a precursor (as shown in Fig. 8a), and it preformed excellent EMWA performance with an ultra-wideband of 8.48 GHz at a thickness of 2.6 mm. The presence of heterogeneous atoms and interfaces provided interfacial polarization centers and defective polarization centers, driving polarization losses into action, resulting in enhancing impedance matching properties. The homogeneous dispersion of Co in the MOF contributed to magnetic loss.177 MnO/Co/C heterogeneous nanocomposites were synthesized by Jiurong Liu's group derived from MnCo-MOF-74 (as shown in Fig. 8b–d), and good performance was achieved with an RL of −68.89 dB, and an EAB of 5.3 GHz. The EMWA performance is mainly attributed to optimized impedance matching, polarization loss (interface polarization, dipole polarization, etc.), natural resonance loss, conductivity loss and multiple scattering.178 Additionally, Jiurong Liu's group synthesized Co/ZrO2/C using Co–Zr-MOF (UIO-66), which showed remarkable EMWA performance with an RL of −57.2 dB, and EAB of 11.9 GHz covering 74.4% of the whole measured bandwidth.179 The introduction of dielectric Co brought new magnetic loss to the already good dielectric loss of the ZrO2/C material, significantly improving the impedance matching performance. Strong interface polarization and the synergistic effect between the multiple components together also contributed to the excellent EMWA performance. Moreover, the Ni/NiO/Cu@C composites derived from Ni–Cu-MOF180 was synthesized, exhibiting a RL of −38.1 dB with only 10 wt% filler loading. The low density of the filler loading can guarantee enhanced conduction loss and impedance matching. Similarly, the introduction of the magnetic dielectric Ni into the monometallic Cu MOF contributes to magnetic loss, while the improved impedance matching, strong interface polarization and the synergistic effect between the multiple components lead to improved EMWA performance. Furthermore, TiO2/ZrTiO4/C composites derived from PCN-415 (TiZr-MOFs)181 has been designed and synthesized, qualified with a RL of −67.8 dB (2.16 mm, 13.0 GHz), and an EAB of 5.9 GHz (2.70 mm). The synergy of enhanced interfacial polarization and other attenuation mechanisms in the composites is revealed.


image file: d4nh00140k-f8.tif
Fig. 8 (a) Schematic diagram of the synthesis process of CoAl-LDO@Co-C, reproduced with permission from ref. 177, Copyright (2021) Elsevier Inc. (b)–(d) SEM images (insets showed the particle size distributions), elemental distribution mapping, and the proposed EMW absorption mechanism of the MOF-derived MnO/Co/C nanocomposites, reproduced with permission from ref. 178, Copyright (2022) Elsevier Ltd.

Dual magnetic metal MOFs, such as CoNi-MOF, CoFe-MOF and NiFe-MOF, have been found to exhibit high impedance matching and excellent EMWA performance. In our previous research, a monometallic Co-MOF was found to have limited EMWA performance. However, by introducing Ni metal to form CoNi alloys, strong magnetic properties were obtained, resulting in enhanced wave absorption performance with an RL of −58.2 dB at 10.62 GHz, and EAB of up to 4.03 GHz (8.80–12.83 GHz).18 In a recent study conducted by Zhai et al., a similar strategy was employed for the synthesis of the Co@NC/Ni nanocomposite. The researchers utilized ZIF67 and Ni(OH)2 precursors, which were subsequently subjected to carbonization at 600 °C (as illustrated in Fig. 9a–g). Notably, the Ni component was sourced from Ni(OH)2, while ZIF67 played a dual role in preventing Ni agglomeration and undergoing natural pyrolysis to yield Ni nanoparticles protected by graphitized carbon. Furthermore, the interface between ZIF67 and Ni(OH)2 imposed constraints on the formation of Co@NC post-ZIF67 pyrolysis. This limitation was attributed to the magnetic nanoparticles' propensity to contribute significantly to the attenuation of the magnetic component in electromagnetic waves.19 Jinxiao Wang's group synthesized a CNT/CoO/Ni2O3 composite derived from a Ni–Co bimetallic MOF, as shown in Fig. 9h–j. The composites exhibited an RL of −49.6 dB and an EAB of 3.87 GHz, which was attributed to the dual electric network formed by Ni3+ and Co2+ energy splitting, and d–d orbital electron transfer.182 Additionally, Zirui Jia's group also obtained a Ni–Co/PC composite derived from a Ni–Co bimetal MOF. The composites exhibited significantly improved EMWA performance with an RL of −67.81 dB and an EAB of 6.16 GHz. This enhancement was attributed to the excellent electrical conductivity, rich surface, high attenuation capability, and the eddy current loss-dominated magnetic loss, all of which contributed to its EMWA performance.183


image file: d4nh00140k-f9.tif
Fig. 9 (a)–(g) SEM images of (a) Ni(OH)2, and (b) S-2, (c) TEM-EDS mapping images of S-2, (d) and (e) 2D and 3D RL plots of S-2, (f) calculated delta value maps of S-2, (g) schematic illustration of the EMWA mechanism for Co@NC/Ni composite. Reproduced with permission from ref. 19, Copyright (2023) Elsevier. (h)–(j) SEM images of CNT/NiCo-600 and CNT/NiCo-MOF-74, EDS results of CNT/NiCo-MOF-74, RL values of CNT/NiCo-600. Reproduced with permission from ref. 182, Copyright (2021) Elsevier B.V.

Hollow CoFe2O4/CoFe@C microspheres were synthesized from Co–Fe MOF, with a focus on crystal transformation, heterogeneous structures, and magnetic exchange coupling, as shown in Fig. 10a–e. The microspheres exhibited strong magnetic saturation (Ms) of 152.4 emu g−1 and optimized RL of −51 dB, with an EAB of 6.0 GHz. These properties were attributed to the synergistic effects of enhancing impedance matching, polarization relaxation, and multi-interfaces.184 Recently, the NiFe@N–C/rGO was synthesized from NiFe-MOF, as shown in Fig. 10f–i. This novel material presents tunable wideband properties and an RL of 72.28 dB, with an EAB of 7.14 GHz, almost covering the whole X and Ku bands. The EWM absorption mechanism was revealed theoretically based on formation energy and dipole moment.185


image file: d4nh00140k-f10.tif
Fig. 10 (a)–(e) Schematic diagrams of the fabrication processes of CoFe2O4/CoFe@C composites, SEM and elemental mapping images of hollow CoFe2O4 composites, hysteresis loops and 2D RL of as-prepared samples, the EMW absorption mechanisms of the CoFe2O4/CoFe@C composites. Reproduced with permission from ref. 184, Copyright (2021) Elsevier. (f)–(i) The schematic diagram of fabricating NiFe@N–C and NiFe@N–C/rGO, SEM images of NiFe-MOF and NiFe@N–C, RL values of NiFe@N–C/rGO-30, magnetic hysteresis loops of as-prepared samples, electron density difference of pyridinic N-rGO structure, rGO functional group EDD details: (1) hydroxyl group; (2) carboxyl group; (3) planar oxygen doping. Electronic localization function of pyridinic N-rGO structure: (4) planar oxygen doping; (5) carboxyl group; (6) hydroxyl group. Reproduced with permission from ref. 185, Copyright (2022) Elsevier.

2.2.2.3 Multi-metallic MOF-based composites. Multi-metallic MOFs offer several advantages over monometallic and bimetallic MOFs by combining the benefits of more than two materials, which enable the construction of multiple topologies that can benefit the EMWA mechanism. In particular, these materials can enhance impedance matching, multiple reflections and scattering, and the presence of interfaces and defect sites that provide polarization losses. The caterpillar-like Co/MnO/CNTs composites derived from Co–Mn–Zn multi-metallic MOF was synthesized by Junying Zhang group, as shown in Fig. 11a–e, which showed strong RL of −58.0 dB and an EAB from 13.52 GHz to 18 GHz, with a thickness of only 1.32 mm, exceeding that of monometallic Co-based MOF materials.186 This improvement was attributed to the integration of electromagnetic dielectric materials to improve permeability, as well as the multi-scale response ability with caterpillar-like structure, and well impedance matching.187 The Lei Wang group has synthesized a novel double-shell-structured MnFe2O4@FeO/C derived from Mn–Fe–Zn multi-metallic MOFs (as shown in Fig. 11f–j). The resulting material exhibits an RL of −53.75 dB with a thickness of 1.8 mm, and the corresponding EAB is 4.74 GHz ranging from 10.27 to 13.90 GHz and 16.89 to 18.0 GHz. By adjusting the Zn-MOF content, the thickness of the carbon layer can be controlled to obtain desirable electromagnetic parameters. The unique construction, expected impedance matching, polarization loss, and strong magnetic loss all contribute to the excellent EMWA performance.188 Furthermore, the Zirui Jia group has synthesized NiCo2−0.5xCr2O3@C nanoparticles based on Ni–Co–Cr multi-metallic MOFs (as shown in Fig. 11k–s). The introduction of additional NiCo2–Cr2O3 has resulted in excellent EMWA performance with an RL of −52.71 dB at 1.6 mm and an EAB of 5.28 GHz at 1.89 mm. The synergistic effect between the appropriate ratio of Cr2O3, NiCo alloy, and good impedance matching optimized by carbon materials contributes to the improved performance.189 More research works are being conducted on multifunctional MOFs that combine the properties of multiple structures and metals.190–193
image file: d4nh00140k-f11.tif
Fig. 11 (a)–(e) Schematic diagram of the growth process of Co/MnO/CNTs, SEM images of Co/MnO/CNTs, EDS mapping images and frequency-dependent RL of the as-obtained Co/MnO/CNTs. Reproduced with permission from ref. 187, Copyright (2020) Elsevier. (f)–(j) TEM and HRTEM of S3 sample, reflection loss of all samples at d = 1.8 mm; the schematic diagram of the microwave absorption mechanism of sample S3. Reproduced with permission from ref. 188, Copyright (2022) Elsevier. (k)–(s) The schematic synthesis process of NiCo2−0.5xCr2O3@C, SEM images of NiCO2−0.5xCr2O3@C Cr0 and Cr0.5, the EDS mapping of Cr0.5. Reproduced with permission from ref. 189, Copyright (2021) Elsevier.

The metallic component within MOF-based composites plays a pivotal role in the realm of EMWA. Researchers have been actively exploring the use of MOF-based composites to create novel heterogeneous interfaces and augment electrical conductivity. The aim is to achieve optimal alignment between the conductive and magnetic properties of the materials and the energy of electromagnetic waves. However, upon a thorough examination of related studies, it becomes evident that MOF-based composites exhibit varying types and quantities of metal centers, resulting in distinctive EMWA performance. A brief overview of EMWA performance of mono-, bi-, and multi-metallic MOF-based composites is reported in Table 2, which includes details such as varying loading amounts, minimum reflection loss, effective absorption bandwidth, and matching thickness. An EMWs is characterized by the simultaneous propagation of electric and magnetic fields. In the context of MOFs, various metals exhibit distinct electronegativity and electronic structures, giving rise to diverse energy band structures and energy level distributions. This variability influences the consumption of electric field energy in EMWs. Lower electronegativity corresponds to improved characteristics in the motion of free electrons. These free electrons can effectively interact with incident EMWs, causing their excitation and the generation of EMWs in the opposite direction. Consequently, this phenomenon reduces the penetration and propagation of the EMWs.

Table 2 MOF-based composites with mono-, bi- and multi-metallic centers for EMWA
Categories Center metal Filler Loading (wt%) RLmin (dB) EAB (GHz) Thickness (mm) Ref.
Mono- Co Co/C-500 40 −35.3 5.8 2.5 78
Co–C-800 30 −62.12 4.6 2.4 77
Co@NCPs 30 −49.8 4.8 2.98 18
Co@CNTs 20 −11.8 1.96 3.3 144
Co/C-650 33 −47.6 5.11 2.0 79
Ni Ni/C 40 −23.4 4.68 1.9 150
Ni@C 30 −55.7 6.0 1.85 152
Ni/C 30 −57.25 5.1 1.8 151
Ni/C@graphene foam 15 −63 5.4 2.1 22
Ni@C-ZIF 40 −86.8 7.4 2.7 156
Fe Fe/C 25 −56.94 6.73 3.1 194
Fe/C-600 40 −22.6 5.3 2.0 159
Fe/C-650 30 −39.43 5.36 2.0 195
Fe/Fe3C@NC 30 −70.8 5.15 2.5 196
Fe/Fe3O4/FeN/NC 30 −60.08 5.06 1.64 162
Mn MnO2@NPC-800 50 −63.21 4.04 2.05 169
Zr ZrO2/C 50 −58.7 5.5 1.7 170
Zn ZnO/NC-700 15 −51.2 4 3.1 171
ZnO/C@PPy 15 −76.31 6.38 2.17 172
Cu CuO/C 50 −57.5 4.7 1.55 173
Cu2S/Cu31S16 20 −15.1 6.2 2.3 174
Ti TiO2/C 40 −49.6 4.6 1.6 175
Bi- CoCd CoCd@CNTs 20 76.6 6.2 2.0 144
CoZn CoZn@CNTs 20 −28.3 3.0 1.8 144
CoZn Co@NC-ZnO 25 −69.6 6.8 2.4 176
CoAl CoAl-LDO@Co-C 30 −38.18 8.48 2.6 177
MnCo MnO/Co/C 50 −68.89 5.3 2.64 178
CoZr Co/ZrO2/C 50 −57.2 6.9 3.3 179
NiCu Ni/NiO/Cu@C 10 −38.1 NA 3.2 180
ZrTi TiO2/ZrTiO4@C 35 −67.8 5.9 2.7 181
CoNi CoNi@NCPs 30 −55.4 4.92 1.74 18
CoNi CNT/CoO/Ni2O3 −49.6 3.87 2.0 182
CoNi NiCo2S4/PC −67.81 6.16 2.1 183
CoFe CoFe2O4/CoFe@C 30 −51 5.9 2.17 184
NiFe NiFe@N–C/rGO-90 20 −55.34 7.14 2.04 185
CoTi CoO/Ti3C2TxMXene-15 5 −52.23 4.88 1.9 191
Multi- CoNiMn CoNi/MnO@C −55.2 8.0 2.1 197
CoMnZn MnO2/ZIF-8@ZIF-67 35 −58.0 5.36 1.97 187
NiCoCr NiCo2−0.5xCr2O3@C −52.71 5.28 1.89 189
CoNiMo H-CoNi@MoC/NC 15 –60.05 3.52 2.5 190
FeCoNi FeCo/FeCoNi@NPC 30 −67 6.24 1.91 192
CoZnMo CoZn/C@MoS2@PPy 30 −49.18 4.56 1.5 193
CoNiTi CoO/NiCo2O4/Ti3C2Tx 10 −58.37 4.24 1.5 191


Furthermore, the distinct size and arrangement of various metals within MOFs result in diverse pore structures, specific surface areas, and crystalline arrangements. This diversity increases the propagation paths of EMWs within MOFs, creating more interfaces for interaction between EMWs and MOF-based composites. Consequently, this facilitates the absorption or scattering of electromagnetic waves at specific frequencies. Monometallic MOFs generally exhibit highly ordered and regular pore structures that contribute to their high specific surface area, enhancing their ability to absorb electromagnetic waves. The increased surface area allows for effective interaction with EMWs, thereby improving shielding efficiency. Additionally, metal ions present in monometallic MOFs, such as those found in Cu-based or Co-based MOFs, can provide conductive pathways, exhibiting good electrical conductivity.

However, monometallic MOFs often have lower mechanical strength and are susceptible to physical damage, which limits their application in EMWA scenarios requiring high mechanical resilience. Furthermore, certain monometallic MOFs may lack stability in humid or corrosive environments, potentially leading to decomposition or loss of functionality over time, thereby restricting their long-term utility in harsh environmental conditions. Additionally, some monometallic MOFs may excel in EMWA within specific frequency bands but exhibit reduced effectiveness in other frequency ranges.

Bimetallic MOFs leverage the synergistic interaction between two different metal ions to establish enhanced conductive pathways, thereby improving overall conductivity and EMWA properties. For instance, the inclusion of copper and nickel as heterogeneous metals in monometallic MOFs enhances both conductivity and EMWA capabilities. The introduction of bimetallic centers also enhances mechanical strength and stability, increasing durability in practical applications. Some bimetallic MOFs exhibit exceptional thermal stability, maintaining structural integrity and performance in high-temperature environments. For example, combinations like Co and Ni maintain robust electrical conductivity and EMWA performance at elevated temperatures.

However, interactions between different metal ions can sometimes impact material performance. Certain metals may preferentially form coordination structures, potentially weakening the properties of the other metal within the MOF. To optimize electromagnetic properties, multiple metal centers can be strategically introduced, enabling precise tuning of electrical conductivity, magnetism, and dielectric constants for efficient EMWA. Multi-metal centers provide diverse active sites that enhance a material's capacity to absorb, reflect, and scatter EMWs across various frequency bands. Popular combinations such as Fe, Ni, and Co exemplify this approach, offering both high electrical conductivity and magnetic properties.

It is noteworthy that MOF-based composites utilized in EMWA applications often feature predominantly magnetic metals, contributing to superior EMWA properties. When the central metal of MOFs is magnetic, as seen with metals such as Co, Ni, and Fe, it typically contains metal ions with unpaired electrons. This characteristic leads to the manifestation of spin magnetic moments in the metal ions, and these moments interact with incident EMWs, influencing their propagation and absorption. Therefore, the deliberate modulation of magnetic metal species in MOF-based composites holds the potential for achieving selective shielding of EMWs.

2.3 Water remediation and air treatment

2.3.1 Water and air pollution. Water is a vital component for all forms of life, and its significance cannot be overstated. However, as the global population increases and industrialization continues to advance, the environment is being subjected to unprecedented levels of pollution.198–202 Despite the importance of economic and social progress, negative consequences have emerged, and the contamination of water has become one of the most complex and critical challenges facing humanity. Various contaminants such as chemical dyes, biopharmaceuticals, personal care products, heavy metal ions, and fluoride are regularly detected in water sources. The effects of light pollutants are manageable and can be addressed. However, heavy pollutants, including toxic and carcinogenic substances, have a devastating and uncontrollable impact on the environment and human health.203–205 Among the organic pollutants, causing water pollution are methylene blue (MB), methyl orange (MO), congo red (CR), rhodamine B (RhB), sulfamethoxazole (SMZ), rose red (RR), and the heavy metal ion Cr(VI).206

Air pollution is a pressing issue that affects the health of living organisms, including humans. The rise of industrialization has resulted in a decline in air quality globally. Industrial emissions that are not effectively treated, as well as pollutants emitted from vehicles, trains, planes and ships, including carbon monoxide, nitrogen oxides, hydrocarbons, and lead, contribute significantly to air pollution. Additionally, second-hand smoke, oil smoke, refrigerators, and air conditioners also contribute this issue. Currently, the main source of air pollution is highly toxic gases and particulate matter (PM), among all air pollutants, volatile organic compounds (VOCs) are the most significant indoor and outdoor pollutants, accounting for 68% of the research conducted on photocatalytic air pollutant treatment. Other hazardous gases, such as H2S, SOx, NH3, NOx, CO, comprise 10% of the research, while particulate matter (PM) accounts for 22%. The air we breathe is vital for our survival, and it is crucial to address the issue of air pollution by mitigating emissions and developing effective treatment methods.206,207

The challenges posed by water and air pollution require a comprehensive and effective approach. Despite numerous methods and techniques having been developed, their success has been limited, and new problems continue to arise. To tackle these complex and evolving issues, it is crucial prioritize methods that are efficient, environmentally friendly, simple and cost-effective. Among these, photocatalytic degradation or reduction of pollutants has gained widespread acceptance due to its reliance on sunlight, a free and abundant energy source.

2.3.2 Introduction of MOF-based photocatalysis. The use of TiO2 as the first catalysts in photocatalysis was a significant breakthrough in the field, which produced electron–hole pairs under UV light, prompting oxidation and reduction reactions.208 Thus, the discovery gives a strategic orientation: the problem of pollutants can be solved as soon as a material, like TiO2 is irradiated by UV light, then a large number of electron–hole pairs are produced to induce rapid oxidation and reduction reactions. However, TiO2 is only sensitive to UV light, which accounts for less than 5% of sunlight, limiting its utilization for sunlight, in which the visible light accounts for nearly 45%. Thus, alternative photocatalysts are explored.209–214 Among them, MOF materials have gained popularity due to the following properties: high specific surface area (over 6000 m2 g−1) providing abundant reaction sites;215 rich topology and tunable porous structure; electron leap platform provided by the metal centers facilitating the separation of electrons and holes in the reaction and thus accelerating the reaction; large-scale expansion and application in industry due to customizable structures. Moreover, MOF-based composites offer a broad range of central metals units and organic linkers that make them a promising option for various photocatalysis production conditions. MOFs act both as solar energy harvesting centers and as organic linkers are irradiated by sunlight, electrons are transferred to the metal centers, which makes MOFs typical semiconductor photocatalyst materials,216,217 making full use of the sunlight in all wavelengths. MOF-based composites have dispersed conduction and valence bands, and can be identified as molecules in a crystalline lattice, which facilitates the leap of electrons from the top of the valence band to the bottom of the conduction band, thus generating holes, and these active species are involved in oxidation and reduction reactions. Zn-, Zr- and Ti-MOF-based composites exhibit semiconductor-like behavior and are particularly useful for photocatalytic performance. In particular, the Zr-MOF-based composites, such as UiO-66 family, are considered attractive for wastewater treatment applications.75 Despite their various advantages presented in the field of photocatalysis, MOFs face challenges in maintaining long-term chemical stability in water, except in acidic or alkaline environments. A review of the performance of monometallic, bimetallic, and multi-metallic MOF-based photocatalysts in the field of photocatalysis is provided.
2.3.3 Water remediation.
2.3.3.1 Monometallic MOF-based composites. Since the first application of Zn-MOF (MOF-5) to treat phenol in water in 2007,74 there has been increasing interest in the use of monometallic MOFs for catalytic degradation of contaminants in water. Monometallic MOF-based composites such as those based on Zn, Fe, Co, Ni, Bi, Cu and Zr have all been employed for this purpose.71–73,218–227 One such example is the Zn-based pillared-layer MOF, NNU-36, which was designed (as shown in Fig. 12a–c) for photocatalytic remediation of water for Cr(VI) reduction and dye degradation under visible light irradiation.71 This unique MOF structure is constructed using Zn–N bonds, with organic linkers playing the main role in absorbing sunlight. Upon absorption of light energy, the catalyst generates a large number of photogenerated electron and hole pairs. These pairs are then transferred through the Zn–N bonds bridge, formed between metals and ligands, to achieve an effective separation of electrons and holes. The separated electrons accumulate at the bottom of the conduction band, while the positively charged holes gather at the top of the valence band, participating in the photocatalytic oxidation and reduction reactions, respectively. As a result of the concentration difference, a continuous flow of electrons and holes are produced, which rapidly move and participate in the photocatalytic reaction (as depicted in Fig. 12c). Despite the effective separation of electrons and holes, their attraction to positive and negative charges leads to recombination, which in turn hampers the photocatalytic efficiency of the system. To address this issue, researchers have developed methods to trap electrons and holes separately, which greatly enhances the photocatalytic efficiency of the system. For example, the Shun Li group synthesized porous ZnO nanocages/rGO/carbon sponge derived from Zn-MOF (ZIF-8) (as illustrated in Fig. 12d–f) for degradation of organic pollutants in the water.72 In this system, the porous nanocages MOF-derived ZnO materials are band-aligned on the rGO surface, where the electrons generated under solar irradiation are injected into the rGO, preventing recombination of electrons and holes left behind. Additionally, the porous structure and high specific surface area increase contact with the reaction target, while the open transport channels promote the transport of electrons and ions and speed up the reaction. Furthermore, the carbon-based materials enhance the absorption of sunlight by the reaction system. These factors contribute to the superior photocatalytic performance exhibited by Zn-MOF derivatives. The zinc-based MOF ZIF-8 was utilized by Sujit K. Ghosh's group to protect hybrid bromide perovskites (HBP) nanocrystals in the degradation of toxic organic pollutants in water, yielding good photocatalytic performance. The sodium-like salt topology of the Zn-based MOF prevented nanoparticles from aggregating or escaping from the framework. The hbp@ZIF-8 composites possess a narrow band gap (2.26–3.1 eV), which indicates good light absorption properties.73 In another study, Co- and Cu-based MOFs were synthesized and utilized for the degradation of MB under visible light (as shown in Fig. 12g–j).218 These MOFs had different metal centers and ligands, leading to varying band gaps. The band gap of the Co-MOF was significantly smaller than that of the Cu-based MOF, suggesting that electrons could more easily leap to the conduction band bottom and achieve effective electron–hole separation. Notably, the photocatalytic process primarily occurred on the surface of the catalyst rather than inside, which is attributed to the larger particle size of MB relative to the pore size of Cu- and Co-MOF.
image file: d4nh00140k-f12.tif
Fig. 12 (a)–(c) FESEM images of as-prepared NNU-36 photocatalysts. Pillared-layer structure of NNU-36, control experiments for the reduction of Cr(VI) under different conditions, control experiments for the photocatalytic degradation of RhB over NNU-36, schematic illustration of photocatalytic reduction Cr(VI) and degradation of dyes over NNU-36 under visible light irradiation, reproduced with permission from ref. 71, Copyright (2017) American Chemical Society. (d)–(f) Schematic illustration of the fabrication process, the SEM and element mapping images of ZnOZIF-8, changes of the characteristic absorption of RhB under different irradiation time using ZRCs, schematic illustration of photocatalytic reaction in ZRCs-based microreactor. Reproduced with permission from ref. 72, Copyright (2018) American Chemical Society. (g)–(j) Perspective view of the complex cation of 1 and 2, the MB degradation under different photocatalytic conditions, a schematic illustration of the energy position and MB degradation over two complexes. Reproduced with permission from ref. 218, Copyright (2021) Elsevier.

2.3.3.2 Bimetallic MOF-based composites. Bimetallic MOF-based composites have been demonstrated to possess more metal sites for ligands than monometallic MOF-based composites. This characteristic gives rise to a multidimensional stereospecific structure that promotes the production of active substances and good conduction channels for enhanced reaction rates. The Fe–Zr-based bimetallic MOF, derived from NH2-UiO-66 MOF (as shown in Fig. 13a–e), was synthesized by Majid Masteri-Farahani's group for water remediation. This MOF-based composite has shown to effectively degrade organic dyes, such as methyl violet 2B, rhodamine B, malachite green, and MB, as well as tetracycline (TC). The dye and TC removal rates were up to 92% and 85%, respectively. The efficient separation of electron–hole carriers is obviously observed after the introduction of Fe into the Zr-MOF, with photogenerated electrons being transferred to Fe–Cr-MOF. This transfer leads to the reduction of Fe3+ to Fe2+, which accelerates the photocatalytic process.228
image file: d4nh00140k-f13.tif
Fig. 13 (a)–(e) FE-SEM images of Fe-UiO-66, photocatalytic degradation of MV in various systems, UV-vis absorption spectra for Fe-UiO-66 + H2O2 + Vis system, photo-Fenton degradation of different organic dyes in the presence of Fe-UiO-66, the possible photocatalytic route for degradation of organic pollutants over Fe-UiO-66 photocatalyst. Reproduced with permission from ref. 228, Copyright (2021) Elsevier. (f)–(i) Schematic representation of the formation of ZnCo-MOF derived ZCO nanocages, FESEM image of ZCO at (a) low magnification, and (b) high magnification, histogram of dye degradation percentage estimated for photo catalytically degraded CV, MB, and RhB dyes in the existence of 50 mg of ZCO nanocages at several illumination times. Reproduced with permission from ref. 229, Copyright (2022) Elsevier.

Indeed, bimetallic MOFs have been found to enhance the efficiency of photocatalytic remediation of water compared to monometallic MOFs. For instance, Zn–Co-based bimetallic nanocages MOF (shown in Fig. 13f–i) were utilized in the photocatalytic removal of organic pollutants, including MB and crystal violet (CV), from water. The nanocages structure of the MOFs provides a large specific surface and reactive sites for superoxide group generation. This in turn, traps photogenerated electrons under visible light and inhibits electron and hole recombination, thereby boosting the photocatalytic performance. The Zn–Co-based nanocages MOF exhibited the 84.3%, 87.9%, and 89.5% of removal of CV, MB, and RhB dye pollutants, respectively.229 A Fe–Sn-based MOF with a core–shell structure was synthesized and its photocatalytic ability was demonstrated by degrading acid red 3R (AR3R) dye in water with 100% degradation efficiency of AR3R within 30 minutes. The effective charge separation, strong photo-response, and rich active sites make a significant contribution the high photocatalytic efficiency of the material. it is also noteworthy that Fe and its oxides possess good ferromagnetism, which facilitates the catalyst's recovery rate, with over 90% after five cycles.230 These findings suggest that the performance of monometallic MOFs with good structural stability and high recovery rates can be enhanced by introducing appropriate metals into the MOF. In addition to these representative bimetallic MOFs, several proliferating MOFs have been widely employed in photocatalysis for water remediation of pollutants in water.231–235 While bimetallic MOFs offer numerous benefits for catalytic reactions, not all metals are suitable for their realization. Catalytic reactions require appropriate reaction sites and effective guiding channels for electron transfer and ion diffusion. Although a bimetallic center creates more metals sites for organic linkers to form ligands, it often comes at the expense of porous structures or guide channels, resulting in the generation of a large amount of reactive material that cannot be quickly transported to participate in the reaction. This not only fails to facilitate the reaction but also inhibits this process.


2.3.3.3 Multi-metallic MOF-based composites. Multi-metal MOF-based composites combine many advantages over mono- and bi-metal ones, including a larger specific surface area, diverse and controllable porous structures, good electron transport properties, and channeling by multiple metals. Bi-based materials are classical photocatalysts in the field of photocatalysis, owing to their unique electronic structure, good light absorption properties, strong redox ability, easily tunable structure, and richer active groups. A novel Zn–Bi–Co based multi-metallic MOFs were synthesized and applied for the treatment of textile wastewater, with CR dye being the primary pollutant. The introduction of Bi and Co metals into the Zn-MOF resulted in better photocatalytic activity (99.6%) for the degradation of CR dye, owing to the newly established interfaces and electron transfer channels that facilitated the transfer of photogenerated electrons while effectively separating them from holes (as shown in Fig. 14a). Furthermore, the introduction of metals into MOFs not only alters their surface morphology, but also increases surface area and the number of active sites, which are all inevitable factors leading to high performance. The superoxide and hydroxyl radicals, which directly depend on the number and separation efficiency of photogenerated electrons and holes, are considered to be the main reactive groups involved in photocatalytic reactions.236 To explore the potential of multi-metallic MOFs in photocatalytic applications, the Vahid Safarifard group synthesized Zr–Ni–Fe based multi-metallic MOFs derived from Zr-MOF (MOF-808) (shown in Fig. 14b–d) focus on meropenem degradation and Cr(VI) reduction. The study investigated the influence of various factors, such as the amount of catalyst, pH, type of scavenger, drug dose on the catalytic performance. The results showed that the highest efficiency of 100% was achieved within 60 minutes at pH = 2 for Cr(VI) reduction and 100% in 60 min for meropenem degradation. Moreover, the catalyst maintained the same degradation efficiency after eight cycles. It is worth noting that Ni and Fe are magnetic metals with a lower bandgap, which facilitates electron transfer, but also easy electron–hole r recombination, thereby inhibiting photocatalytic performance. It was found that the best performance was obtained at a ferrite: MOF ratio was 1[thin space (1/6-em)]:[thin space (1/6-em)]2, and the introduction of magnetic metals also enhanced the catalyst recovery rate.237
image file: d4nh00140k-f14.tif
Fig. 14 (a) Photocatalytic mechanism of MOF-5/BiCoO3 composite under light irradiation. Reproduced from ref. 236. (b)–(d) FE-SEM images of samples NiFe2O4/MOF-808, time-dependent plot for NiFe2O4, MOF-808, NiFe2O4/MOF-808 (1[thin space (1/6-em)]:[thin space (1/6-em)]1.5, 1[thin space (1/6-em)]:[thin space (1/6-em)]2 and, 1[thin space (1/6-em)]:[thin space (1/6-em)]3), Proposed mechanism of photocatalytic performance by NiFe2O4/MOF-808 composite, reproduced with permission from ref. 237, Copyright (2022) Elsevier. (e) Plausible photocatalytic mechanism of MO degradation by porphyrin-sensitized TiO2@Cd-MOF nanocomposite aerogel heterogenous photocatalyst, reproduced with permission from ref. 238, Copyright (2022) Elsevier.

Pure TiO2 is known for its limited photocatalytic performance and low utilisation of sunlight. Recently, X. Sahaya Shajan's group synthesized Zn–Ti–Cd based multi-metallic MOF nanocomposite aerogels and evaluated their photocatalytic performance in the degradation of methyl orange (MO) and 2-mercaptobenzothiazole (MBT) dye, with maximum degradation efficiency of 94.1% for MO dye. The enhanced performance of the nanocomposite aerogels can be attributed to the generation of multiple interfaces, enhanced light utilization, and efficient electron injection (shown in Fig. 14e).238 The construction of polymetallic MOF-based composites by introducing magnetic or non-magnetic metals to improve photocatalytic performance has been tried from the past to the present,239,240 but the development of new MOF-based composites is limited, and it is therefore essential to optimize the use of the existing ones.

The use of MOF-based composites as photocatalysts for water remediation holds great promise. Their multi-void and high specific surface area properties provide numerous reactive sites for photocatalytic reactions. Notably, the customizable nature of MOF-based composites, with various metal centers and tunable photo responsiveness, renders them highly prospective as photocatalysts. Table 3 presents a concise overview of the photocatalytic water remediation performance of monometallic, bimetallic, and multi-metallic MOF-based composites. The table includes key parameters such as the type and concentration of pollutants, catalyst amount, catalytic time, and photocatalytic efficiency. Monometallic MOFs typically exhibit high specific surface area and a well-defined pore structure, facilitating efficient pollutant adsorption and exposure of photocatalytic active sites, thereby enhancing photocatalytic efficiency. Metals such as Ti, Zn, and Fe within these MOFs demonstrate robust photocatalytic activity under UV irradiation, generating sufficient electron–hole pairs to initiate pollutant degradation in water. Furthermore, monometallic MOFs generally possess favorable chemical stability that persists throughout the photocatalytic process, while their structures and properties are relatively straightforward to manipulate and optimize. Nonetheless, their limited light absorption and increased propensity for electron–hole pair recombination highlight the rationale for exploring multi-metal MOFs.

Table 3 MOF-based composites with mono-, bi- and multi-metallic centers for photocatalysis (water)
Categories Center metal Catalyst Pollutant C pollutant (mg/L) M catalyst (mg) Time (min) η (%) Ref.
Mono- Zn MOF-5 Phenols 40 80 25 50 74
NNU-36 Cr(VI) 10 15 60 95.3 71
RhB 70 96.2
MB 80 94.2
R6G 90 93.5
ZnO/C RhB 10 50 120 89 72
ZIF-8 Methyl orange (MO) 0.3 2 100 <10 73
ZnO@ZIF-8 MB 10 10 240 94.1 241
Cu [Cu3(L)2(4,4′-bipy)] MB 10 40 100 81.17 222
[Cu(4,4′-bipy)Cl]n 10 4 150 93.93 218
Co [Co(4,4′-bipy)·(HCOO)2]n 10 54.7
Ce Ce-MOF RhB 10 30 12 99 220
Tb Tb-MOF 10 30 24 95
Dy Dy-MOF 10 30 60 90
Cr MIL-53 MB 0.13 1 60 32 226
Al 60 30
Fe 20 20
Fe3O4@MIL-100 10 10 180 93.93 242
Ti NH2-MIL-125 MB 120 56 224
Sodium fluorescein (SF) 60
RhB 33
Bi- FeZr Fe/NH2-UiO-66 Tetracycline (TC) 20 10 60 85 228
Methyl violet 2B 160 87.1
RhB 87
Malachite green 74
MB 84
ZnCo ZnCo2O4 Crystal violet (CV) 10 50 180 84.3 229
MB 87.9
RhB 89.5
FeSn Fe3O4@Sn-MOF AR3R 30 100 230
BiCu Bi2O3/MOF/GO RhB 10 50 60 85 234
CuCr CuCr2O4/CuO MB 10 20 35 90 233
TC 120 95
CoFe Fe/MIL-53-NH2 Bisphenol A (BPA) 50 5 150 100 232
CoFe CoFe2O4/Fe2O3 TC 30 10 80 99.7 231
BPA 98.1
SMX 94.8
DFC 97
IBP 96.1
OFX 96.5
CuFe MIL 53(Fe–Cu) Ciprofloxacin 15 25 70 57.88 235
Multi- ZnBiCo MOF-5/BiCoO3 Congo-red (CR) 25 10 90 99.6 236
NiFeZr NiFe2O4/MOF-808 Cr(VI) 10 15 60 100 237
ZnTiCd Zn/TiO2@Cd-MOF Methyl orange (MO) 10 10 60 97.4 238
CoNiCuW MOF/CuWO4 MB 10 135 98 240
4-NP 105 81
ZnBiFe MOF/BiFeO3 MB 20 30 100 93 239


MOF-based composites with diverse metal centers exhibit distinct electronic structures and light-absorbing abilities, resulting in a broad and effective light-absorbing range encompassing both visible and UV regions—a critical characteristic for effective photocatalysis. Multi-metallic MOFs feature multiple active sites capable of simultaneously providing photocatalytic, catalytic, and adsorption capacities, expanding their applicability across various water pollutant types. However, the synthesis of multi-metallic MOFs is inherently complex, and interactions between different metal ions within these frameworks can potentially hinder overall material performance and stability. Therefore, rigorous optimization and control are essential during the design and synthesis phases to ensure optimal functionality and durability of the materials. Furthermore, the efficiency of photocatalysis in water remediation is influenced by the lifetime of the excited state after the photoexcited catalytic reaction. The judicious selection and modulation of metal centers in MOF-based composites can extend the excited state lifetime, significantly enhancing catalytic performance. The energy levels of catalytically active sites are intricately linked to the electronic energy levels of metal centers, and an optimal alignment between the two facilitates more facile electron transfer. The selection of metal centers, in general, plays a significant role in determining the stability of MOF-based composites catalysts. Certain metals exhibit heightened sensitivity to light and chemical environments, making them more susceptible to degradation. For sustained efficacy in photocatalytic water remediation applications, the development of MOF-based composites with long-term stability is crucial.

2.3.4 Atmosphere purification.
2.3.4.1 Monometallic MOF-based composites. Recently, Yun Hu's group synthesized a Fe-based monometallic MOF (MIL-100) photocatalyst (as shown in Fig. 15a–e) for the degradation of a toxic VOC (acetaldehyde) and for bacteriostasis against Escherichia coli in indoor applications. The abundant exposure of unsaturated Fe2+ active sites lead to high catalytic performance by promoting the separation of photogenerated electrons and holes, thus participating in redox reactions. Superoxide groups are generated by the reaction of adsorbed oxygen with photogenerated electrons, while Fe2+ ions act as a mere bridge for electron transport, rather than as a beneficiary, as evidenced by the absence of reduced Fe+. This abundant Fe2+ active sites could reduce O2 to H2O through a 4-electron pathway.67 The conversion between Fe3+ and Fe2+ plays a crucial role in the separation of photogenerated electron-holes, which makes Fe-based MOFs unique. This property was also exploited by Xiao Wang's group to achieve effective treatment (over 80% for degradation of xylenes and styrene) of gaseous BTXS (benzene, toluene, xylenes and styrene) pollutants with large molecular sizes using a photocatalyst based on Fe MOF (MIL-100). In addition to the properties of Fe ions, the micro- and mesopores (2–10 nm) in Fe-based MOFs yield a large number of active sites for catalytic reactions, and the unsaturated acidic Fe3–O sites facilitated the capture of BTXS molecules (as shown in Fig. 15f).70 A novel synthetic strategy for the synthesis of an acidic Ti-based MOF (MIL-125) for the degradation of chlorobenzene and toluene under visible light irradiation, which exhibited excellent photocatalytic properties by mineralizing 80% of pollutants in a shorter period of time, with a still impressive efficiency of over 90% after four cycles. Superoxide groups and hydroxyl radicals were identified as the main reactive oxygen radicals during photocatalytic reactions.66 Another notable study by Taicheng An's group focused on the synthesis of a novel porous nickel foam (Ni-MOF/NF) (as shown in Fig. 15g–h), for the degradation of ethyl acetate, which achieved a remarkable removal efficiency of 98.1% and a mineralization efficiency of 86.6%. The high exposure of active sites, strong light absorption centers, and fast electron and mass transport channels and pathways in the Ni-based MOF foam were attributed to its excellent photocatalytic removal efficiencies for typical VOCs emitted from the paint spray industry.69 The Zn-based MOF (ZIF-8) has also shown promising results, exhibiting >99.99% photocatalytic killing efficiency against airborne bacteria in 30 min and 97% particulate matter (PM) removal under visible light.68 Additionally, Fe-, Zr-, and Re-MOF-based composites have been highly effective for the removal of toluene, ozone, 2-chloroethyl ethyl sulfide (CEES), carbon dioxide (CO2, CO etc.), which are common polluting gases in everyday life.243–247
image file: d4nh00140k-f15.tif
Fig. 15 (a)–(e) SEM images, and the mechanism for photocatalytic oxidation on M-300 catalyst under visible light, E. coli removal rate under the visible light and photocatalytic performance of acetaldehyde degradation under the sunlight, reproduced with permission from ref. 67, Copyright (2023) Elsevier. (f) The mechanism of photocatalytic degradation of BTXS on the MIL-100(Fe) MOF/MOX homojunctions. Reproduced with permission from ref. 70, Copyright (2021) Elsevier. (g) and (h) Illustration of the in situ preparation of Ni-MOF/NF, SEM images of Ni-MOF/NF, reproduced with permission from ref. 69, Copyright (2020) RSC Pub.

2.3.4.2 Bimetallic MOF-based composites. MOFs with bimetallic centers have been found to perform better than those with monometallic centers in response to airborne contaminants. This is due to a fundamental increase in electron channeling and faster movement. Toluene diisocyanate (TDI) and methylene diphenyl diisocyanate (MDI) are semi-volatile organic compounds and account for more than 90% of the isocyanate family in the world's total consumption. In recent research conducted by Majid Kermani's group, Bi–Ti-based bimetallic MOF-based composites were synthesized for degradation of TDI and MDI in the air. The results of this study showed that the bimetallic MOF-based composites were able to degrade more than 90% of isocyanates with synergistic effect coefficient of 2.03 and 2.34 for TDI and MDI, respectively. Interestingly, the removal rate using air as a carrier was found to be 61.7%, while in pure oxygen it was 80.8%.248 Vahid Safarifard and colleagues synthesized a Co–Zn-based MOF for enhancing the photocatalytic aerobic oxidation of benzyl alcohol. The bimetallic MOF-based composites were prepared through metal ion exchange and effectively improved the photocatalytic performance for benzyl alcohol oxidation. The introduction of new metal ions increases the energy level in the conduction band of the original catalyst and facilitates the jump of electrons from the top of the valence band to the conduction band. Co acts as electron traps and immobilizes photogenerated electrons, which are then rapidly transferred to react with oxygen to produce super-positive groups.249 In the same year, Vahid Safarifard's group also demonstrated that the Co–Zn-based bimetallic MOF-based composites exhibit good photocatalytic properties in aerobic oxidation of benzyl alcohol to benzaldehyde (as shown in Fig. 16a–e). The effective separation of photogenerated electron–hole pairs and good light absorption are considered to be the main factors, which of course cannot be achieved without the role of Co and Zn bimetallic centers. The electrons and holes serve as the main reactive species.250 Moreover, the Co–Fe-based bimetallic MOF-based composites with dye-sensitized were synthesized by Zhengquan Li and coworkers for photocatalytic CO2 reduction (as shown in Fig. 16f–i). The introduction of Ru metals facilitated the injection of photogenerated electrons into Fe-MOF, resulting in a negative shift of −0.15 V (vs. RHE) in its LUMO potential. This bimetallic MOF-based composites showed excellent photocatalytic performance with CO2-to-CO activity of 1120 μmol g−1 h−1. Additionally, Co metal ions were used to adapt the electronic structure of Fe-MOF, resulting in a remarkable photocatalytic activity of 1637 μmol g−1 h−1.251 In another study, the Fe–Ni MOF (as shown in Fig. 16j–o) was used for removal of hazardous indoor VOCs, achieving average adsorption and removal rates of 94.25% and 75.95%.252 There are numerous examples of improved catalytic performance of MOF-based composites catalysts through the introduction of different metals. These improvements can be attributed to various factors, such as changes in electronic structure, electron transport channels, absorbance, and multivalent metal ion conversion for electron transfer.252–259
image file: d4nh00140k-f16.tif
Fig. 16 (a)–(e) The schematic diagram for the synthesis of g-C3N4-Co, and (b) fabrication of TMU-22/g-C3N4-Co composite, the model reaction for photocatalytic aerobic oxidation of benzyl alcohol to benzaldehyde, SEM of TMU-22/g-C3N4-Co composite, checking the effect of composite composition and solvent. Reproduced with permission from ref. 250, Copyright (2022) Elsevier. (f)–(i) TEM image of the Co–Fe-MNS catalyst, photocatalytic CO production of 2D Fe-MNS, Dye, Dye/Fe-MNS, and dye/Co–Fe-MNS, time-dependent photocatalytic activities over different samples. Reproduced with permission from ref. 251, Copyright (2021) Elsevier. (j)–(o) A schematic of the electrophoretic deposition setup, the fabricated MIL-100(Fe)-based PMF, a scheme showing the photocatalytic decomposition of VOCs on to the PMF, the adsorption cycling test (top) and the removal performance (bottom) for 50 cycles. Reproduced with permission from ref. 252, Copyright (2021) Elsevier.

2.3.4.3 Multi-metallic MOF-based composites. Taicheng An and colleagues synthesized Z-scheme Au–Ti–Zr based multi-metallic MOF-based composites for photocatalytic degradation of ethylacetate (as shown in Fig. 17a–e). The incorporation of Au directly broadens the light absorption range from the UV to the visible region, which is attributed to Au's excellent localized surface plasmon resonance properties. Moreover, the ultrafine Au species serve as an electron mediator, facilitating the transfer of photogenerated electrons and thereby enhancing the separation efficiency of photogenerated electron pairs. This efficient separation process accelerates the generation of reactive groups, such as superoxide, hydroxyl radicals, reaching 85%VOCs mineralization and 94.6% ethyl acetate degradation efficiency.260 Au–Ti–Zn-MOF-based composites were synthesized by Wenxin Dai and colleagues for the catalytic oxidation of CO at room temperature (as shown in Fig. 17f–l). Notably, while the base MOF was substituted, it is reasonable to expect that the resulting catalyst structures would be distinct from aforementioned multi-metal MOF-based composites catalysts with using of Au and Ti. Particularly, ZIF-8 MOF is known to enhance the roughness of this composite catalyst, thereby preventing Au migration and aggregation. Additionally, ZIF-8 with abundant delocalized electrons of π bond could act as an electron donor and provide multiple electron transport channels that accelerate the transport of photogenerated electrons, and these behaviors together contribute to good photocatalytic performance.261 Multi-metallic MOF-based composites applications are relatively limited due to the constraints posed by the synthesis and use of these catalysts in the air-catalyzed reactions. Specifically, only a limited number of species can be synthesized and used for catalytic reactions in air. Furthermore, metal ions have to be protected from oxidation to ensure an abundance of reaction sites, which becomes an increasingly challenging achievement as the number of metal species in MOFs increases. Precious metals are often favored to meet these conditions, but this comes at a high cost.
image file: d4nh00140k-f17.tif
Fig. 17 (a)–(e) Illustration of the preparation of the Au–TiO2@NH2-UiO-66 nanocomposite, HAADF-STEM images, removal efficiencies (a) and mineralization efficiencies (b) of ethyl acetate during photocatalytic oxidation, possible reaction mechanism for the photocatalytic oxidation of ethyl acetate over Au–TiO2@NH2-UiO-66 under visible light irradiation. Reproduced with permission from ref. 260, Copyright (2021) Royal Society of Chemistry. (f)–(l) SEM and TEM images of Au/ZIF-8-TiO2, thermogravimetry pattern of samples, the possible charge transfer behavior among Au, TiO2 and ZIF-8 during the process of forming Au/ZIF-8-TiO2 structure, proposed schematic of electron transfer among Au, TiO2 and ZIF-8 sites over Au/ZIF-8-TiO2 under visible light irradiation. Reproduced with permission from ref. 261, Copyright (2017) Elsevier.

For photocatalytic degradation of hazardous gases in air, in addition to a large specific surface area providing sufficient reactive sites for the generation and effective separation of electron–hole pairs, additional features are necessary such as: (a) a highly tailored pore structure to improve adsorption efficiency, (b) faster electron transport, (c) sufficiently high stability against humidity, temperature, and gas influencing factors, attributing to the different environments in which the reaction occurs, with gases having a large free diffusivity as well as the presence of lower concentrations of hazardous gases. A brief overview of performance of monometallic, bimetallic, and multi-metallic MOF-based composites in the photocatalytic degradation of hazardous atmospheric gases is reported in Table 4. Pollutant type and concentration, amount of catalyst, reaction time and photocatalytic efficiency are listed into it.

Table 4 MOF-based composites with mono-, bi- and multi-metallic centers for photocatalysis (air)
Categories Center metal Catalyst Pollutant C pollutant (ppm) M catalyst (mg) Time (h) η (%) Ref.
Mono- Fe M-300 VOCs (acetaldehyde, acetone) 1 25 360 >90 67
MIL-100(Fe) MOF/MOX Benzene 25 50 140 23 70
Toluene 41
Xylenes 83.1
Styrene 83
NH2-MIL 101(Fe) Gaseous toluene 4 20 600 79.4 243
MIL-100(Fe) Ozone 45 30 6000 100 245
Ti P-NH2-MIL-125 Chlorobenzene 1 10 60 100 66
Toluene 20 96
Ni Ni-MOF/NF Ethyl acetate 70 360 98.1 69
Zn Zn-MOF PM 50 30 97 68
Zr NH2-UiO-66 Ethyl acetate 70 100 360 95.3 260
Bi- CoZn TMU-22(Zn/Co) Benzyl alcohol 0.5 60 250 73 249
TMU-22/g-C3N4-Co Benzyl alcohol 1 20 300 75 250
TiBi BiOI@MOF/zeolite Toluene-diisocyante 10 180 98.7 248
Methylene diphenyl diisocyanate 95.6
TiZn ZIF-8 derived carbon-TiO2 Toluene 25 76 262
TiCr TiO2/MIL-101(Cr) Formaldehyde 8 200 80 258
o-Xylene 0.2 82
5.0-TMCr-60 Toluene 25 480 91.4 254
TiZr TiO2@ NH2-UiO-66 (Zr) Gaseous styrene 30 80 90 255
TiO2@NH2-UiO-66 Ethyl acetate 70 100 360 93.2 260
Multi- AuTiZr Au–TiO2@NH2-UiO-66 Ethyl acetate 70 100 360 94.6 260
ZnAuTi Au/ZIF-8-TiO2 CO 2.5 50 261


The overall performance of monometallic MOF-based composite photocatalysts for the degradation of hazardous gas molecules in air is significantly weaker than that of bimetallic MOF-based composites. Many single-metal-centered MOFs exhibit significant photocatalytic activity primarily in the ultraviolet spectrum, which comprises a minor portion of sunlight. This restricts their utility in the visible spectrum, necessitating material modifications to broaden their light absorption capabilities. While the metal ions within mono-metallic MOFs serve as active sites, effectively capturing light energy and initiating electron–hole pair generation, the propensity for electron–hole recombination during photocatalysis diminishes their efficiency. Therefore, strategic material design and modification are imperative to mitigate electron–hole complexation and bolster photocatalytic efficacy. In particular, the lower catalytic efficiency of Fe based monometallic MOF-based composites may be attributed to the fact that metal Fe has lower common oxidation states, i.e., +2 and +3 valence states, and usually higher oxidation states imply easier electron transfer phenomena. Whereas monometallic MOF-based composites with higher common oxidation states such as those with Ti (+2 and +4) and Zr (+4) exhibited higher photocatalytic performance under lower pollutant concentrations. This is attributed to the fact that monometallic MOF-based composites have only one metal center, which implies limited light absorption, electron generation and transfer capability.

On the contrary, bimetallic MOF-based composites have two different metal centers, the synergistic effect between them can improve the ability of light absorption, electron transfer and generation of reaction intermediates, thus achieving higher photocatalytic performance. In addition, the two heterogeneous metal centers slow down the compounding rate of electron–hole pairs, attributing to that the introduction of multi metals can create different electronic energy levels, thus facilitating the separation of photogenerated electrons and holes, furtherly increasing the lifetime of photogenerated electrons and holes, and improve the photocatalytic efficiency. Various metal centers offer diverse active sites that can augment the capture and degradation of pollutants. For instance, the combination of Pt and Au can yield exceptional catalytic activity, whereas iron and cobalt can improve magnetic separation capabilities.

Therefore, Ti elements with higher oxidation states are mostly used in bi- and multi-metallic MOF-based composites to form a synergistic effect to achieve better photocatalytic efficiency at low concentrations of pollutants. The few research works on MOF-based composites photocatalysts with multi-metal centers have shown that more metal centers are often accompanied by more complex structures, thus complicating the generation of multiple effects, which can further limit practical applications.

3. Conclusions and perspectives

This review provides a critical assessment of the recent advancements in MOF-based composites featuring monometallic, bimetallic, and multi-metallic centers, with a focus on their applications in detecting, absorbing, and degrading environmental pollutants. The components tunability of MOF-based composites by selecting and tailoring metal centers allows them to meet the needs of specific applications. Specifically, the discussion centers on their efficacy in hazardous gases sensing, EMWA, and the degradation of pollutants in both aqueous and atmospheric environments. Among them, the molecular sieve effect being considered unique in MOF-based composites with network structure of large and small pores are employed for hazardous gases sensing applications. The multi-channel structures are designed in the MOF-based composites by changing the chosen metals and post-treatment processes to enhance conductive and magnetic properties for EMWA, and rich active site and electron transport properties for degradation of pollutants in both aqueous and atmospheric environments.

In the following points, more specific conclusions and perspectives are provided:

(1) Employing only one type of metal may result in relatively low selectivity, limiting the material's capability to discern and detect specific gases. The incorporation of certain additional metal ions into MOFs evidently enhances their performance in hazardous gases sensing. However, challenges related to structural instability arise from mismatches between the incorporated metals. Relatively intricate synthesis processes lead to high production costs, restricting further applications.

(2) Multi-metallic MOF-based composites are very limited in hazardous gases sensing applications. Different factors limit sensor applications, such as the stability of multi-metallic MOFs, especially in high temperature or humidity environments for gas sensing, the structural damage or inactivation of the active sites of polymetallic MOFs. Moreover, no study has yet been able to demonstrate that the multi-metallic MOFs exhibit obvious advantages in terms of hazardous gas sensing compared to mono- and bi-metallic MOFs. The latter are highly favored due to easier synthesis methods and better structural stability.

(3) The material prerequisites for MOFs in EMWA encompass two main aspects. Firstly, the central metal must possess magnetic properties to effectively absorb the magnetic component of the EMWs. Secondly, the adoption of a multi-channel design is essential to enhance conductivity characteristics. Consequently, the design focus shifts towards the incorporation of multiple metals, with emphasis on magnetic metals, such as Co, Ni, and Fe. This strategic utilization of multi-metal MOFs, particularly those endowed with magnetic properties, holds considerable promise in advancing the performance of EMW absorbers.

(4) Relying solely on dielectric losses or magnetic losses would be unwise, but combination of magnetic and dielectric-based MOFs could potentially overcome the limitations of a lack of magnetism and make it the best option in the EMWA field. Furthermore, multi-metallic MOFs are capable of covering a broader range of EMW frequencies. This is attributed to the unique electronic structures and magnetic properties of the various metals involved, which enable these materials to absorb both low and high-frequency EMWs. The presence of multiple metal in MOFs enhances both dielectric loss and magnetic loss through the synergistic interactions among the different metals. Dielectric loss results from the energy dissipation during the polarization process within the material, while magnetic loss arises from the magnetization process of the magnetic metals. The integration of these two mechanisms significantly enhances the EMWA performance.

(5) Multi-metallic MOFs can absorb EMWs through various mechanisms, including conductive loss, magnetic loss, dielectric loss, and multiple scattering. The combination of different metal centers and organic ligands generates multiple absorption mechanisms, further enhancing the materials' absorption efficiency. For instance, the presence of heterogeneous atoms and interfaces provided interfacial polarization centers and defective polarization centers, driving polarization losses into action, resulting in enhancing impedance matching properties.

(6) By adjusting the types and ratios of metal ions and organic ligands, the physical and chemical properties of MOFs—such as electrical conductivity, magnetic permeability, and dielectric constant—can be precisely tuned to optimize their EMWA properties. However, structural stability and durability pose significant challenges for multi-metallic MOFs, particularly at high temperatures or under strong electromagnetic field environments. Ensuring the consistency and reproducibility of the performance of multi-metallic MOFs in large-scale production remains a difficult task, confining their application largely to experimental research stages.

(7) MOFs with diverse metal centers result in a broad and effective light-absorbing range encompassing both visible and UV regions—a critical characteristic for effective photocatalysis. Furthermore, the efficiency of photocatalysis in water remediation is influenced by the lifetime of the excited state after the photoexcited catalytic reaction. The judicious selection and modulation of metal centers in MOFs can extend the excited state lifetime, significantly enhancing catalytic performance, attributing to different metal centers exhibit different electron affinities and conductivities.

(8) A highly tailored pore structure to improve adsorption efficiency, faster electron transport, and a sufficiently high stability to against humidity, temperature, and gas influencing factors are necessary as MOF materials under different environments in which the reaction occurs, with gases having a large free diffusivity as well as the presence of lower concentrations of hazardous gases.

(9) Multi-metallic MOF applications are relatively limited due to the constraints posed by the synthesis and use of these catalysts in the air-catalyzed reactions. The synthesis of multi-metallic MOFs is complex and not ideal when strict microstructural and phase homogeneity are required. Additionally, multi-metallic MOFs may experience dissolution or reorganization of metal ions during the reaction process, resulting in partial structural collapse or reduced activity. The use of multiple metal precursors in the synthesis further increases material costs and process complexity. Furthermore, metal ions have to be protected from oxidation to ensure an abundance of reaction sites, which becomes increasingly challenging as the number of metal species in MOFs increases. Precious metals are often favored to meet these conditions, but this comes at a high cost.

Data availability

Data sharing is not applicable to this review manuscript “Multi-Metallic MOFs based Composites for Environmental Applications: Synergizing Metal Centers and Interactions” as no datasets were generated or analysed during the current review work.

Conflicts of interest

The authors declare that they have no known competing financial interests or personal relationships.

Acknowledgements

The authors acknowledge the funding support from the financial support by China Scholarship Council (202106970006). The authors also acknowledge the 6G-life project (project no. 16KISK001K), VolkswagenStiftung project (grant no. 96632, 9B396), EU project “SMELLODI” (grant no. 101046369), the SAB project “KoMMet” funded by the State Ministry of Science and Cultural Affairs of Saxony, Germany (grant agreement ID: 100715133), and Cluster of Excellence “Centre for Tactile Internet with Human-in-the-Loop” (CeTI, project ID 390696704) of TUD Dresden University of Technology for support.

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