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Iron single-atom/clusters catalysts derived from iron-rich Enteromorpha after urea-saturation for Fenton-like reaction
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Yujie Zhang, Siyi Liu, Dongdong Chen, Xing Xu*
Chinese Chemical Letters | 2024, 35(3) : 108666
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Chinese Chemical Letters | 2024, 35(3): 108666
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Iron single-atom/clusters catalysts derived from iron-rich Enteromorpha after urea-saturation for Fenton-like reaction
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Yujie Zhang, Siyi Liu, Dongdong Chen, Xing Xu*
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  • School of Environmental Science and Engineering, Shandong University, Qingdao 266237, China
Published: 2024-03-15 doi: 10.1016/j.cclet.2023.108666
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Fabrication of single atom catalysts (SACs) by a green and gentle method is important for their practical Fenton-like use. In this work, a high effective iron-based catalyst was prepared from the iron-rich Enteromorpha for NPX degradation via peroxymonosulfate (PMS). Both Fe-SACs and iron-clusters was fabricated from the intrinsic iron element in Enteromorpha after the urea saturation. The Fe-SACs/clusters can achieve 100% of NPX oxidation within 20 min with the kobs of 0.282 min−1. Quenching tests indicated that the radical pathways were not dominated in the catalytic systems, and strong electron transfer process can be induced in the Fe-SACs/clusters + PMS system by using the NPX as electron donor and Fe-SACs/clusters/PMS* complexes as electron acceptor. This result was consistent with the phenomenon observed in the galvanic oxidation system. In addition, the Fe-SACs/clusters was deposited onto the ceramic membrane (CM) by the spraying-crosslinking process to form a Fe-SACs/clusters@CM, which showed an effective and continuous NPX degradation in a heterogeneous PMS system.

SACs  /  Iron  /  Clusters  /  Fenton-like reaction  /  Enteromorpha
Yujie Zhang, Siyi Liu, Dongdong Chen, Xing Xu. Iron single-atom/clusters catalysts derived from iron-rich Enteromorpha after urea-saturation for Fenton-like reaction[J]. Chinese Chemical Letters, 2024 , 35 (3) : 108666 - . DOI: 10.1016/j.cclet.2023.108666
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Advanced oxidation process (AOPs) can completely mineralize or decompose most of the refractory organic pollutants in water/wastewater, which has shown a promising application prospect [1,2]. Compared with the traditional AOPs, the novel AOPs based on persulfate (peroxymonosulfate (PMS), and peroxodisulfate (PDS)) activation exhibit the advantages such as long half-life, high redox potential and wide application pH range, which makes the technology stand out in the process of treating refractory organic pollutants [3,4]. Recently, the construction of an efficient heterogeneous catalytic system is the main research direction of PMS oxidation technology. The key is to design heterogeneous catalysts with high activity and stability to activate PMS for wastewater treatment [5,6]. the current research goal is to design low-cost heterogeneous catalysts with good stability and avoid secondary pollution to achieve efficient degradation of pollutants [7–10].
Single atom catalysts (SACs) have extremely high catalytic activity, which can expose the active metal sites to the maximum extent, and break the limitations of traditional catalytic processes on kinetics and catalytic activity, which has become a research hotspot in the field of AOPs [11–13]. Currently, various synthesis strategies (pyrolysis, wet chemical synthesis, physical and chemical vapor deposition, electrochemical deposition, ball milling, etc.) have been used to prepare multifunctional SACs [14–18]. However, most current preparation processes for SACs are complex and cost sensitive. The primary key to the AOPs-based catalysts is the cost requirement [19–21]. Complex and expensive catalysts are usually not preferred for advanced oxidation applications. As a result, a green and low-cost strategy is required for the fabrication of AOP-based SACs.
As a transition metal, iron is widely found in many biomass materials in nature. Among them, the iron content of Entermorpha is as high as 0.2–0.5 wt%, which is much higher than that of other Marine algae and other biomass materials [22]. Enteromorpha is a kind of seasonal Marine pollution algae, can lead to bloom, produce toxic metabolic waste to Marine organisms, consumption of dissolved oxygen, cause great impact on the coastal ecological environment. Especially in Shandong coastal cities, the problem of seasonal pollution of Enteromorpha is particularly serious, which has become one of the key points of Marine pollution monitoring and control in recent years. It was found in the previous study that the polysaccharides, proteins and other nitrogen compounds in Enteromorpha can coordinate with abundant iron elements in Enteromorpha under the condition of high temperature pyrolysis [22]. Without the addition of nitrogen sources and metal precursors, atomic cluster catalysts with a high iron loading capacity of 0.87–1.35 wt% can be prepared [22]. The metal load is comparable to that of most SACs reported so far. Due to the low nitrogen content in Enteromorpha and its weak anchoring effect on iron, only ~10% of the iron in Enteromorpha was transformed into the dispersed iron atoms, while 90% of the iron elements in Enteromorpha gather in the carbon layer structure in the form of iron clusters [22]. Because the SACs mainly relied on the number of dispersed metal atoms to achieve its ultra-high catalytic activity, therefore, how to improve the atomic dispersion of high content iron elements in Enteromorpha is the key to achieve the large-scale preparation and efficient application of Enteromorpha based Fe-SACs.
In this work, the iron-based catalyst was prepared from the iron-rich Enteromorpha which was collected from the Qingdao harbor, Shandong province. The dried Enteromorpha was first mixed with 1 mol/L of urea solution for saturating the dried Enteromorpha with urea, which could increase the dissolved nitrogen content in the Enteromorpha (Fig. 1). The urea-saturated Enteromorpha was then freeze dried and pyrolyzed to obtain the iron-based catalyst with improved dispersion of iron atom and reduced amounts of iron-clusters (Fe-SACs/clusters).
The X-ray absorption fine structure (XAFS) can provide the accurate coordination structure in the metal-based catalyst [23–25]. The Fe K-edge X-ray absorption near-edge structure (XANES) spectra of Fe-SACs/clusters catalysts and standard samples was given in Fig. 2a. Result indicated that the state of Fe in the Fe-SACs/clusters was located between Fe(Ⅱ) and Fe(Ⅲ). The coordination number of the Fe-SACs in as-prepared catalysts was determined by the Fourier transform- extended X-ray absorption fine structure (FT-EXAFS) spectra (Fig. S2 in Supporting information). The fitting parameters were given in Table S1 (Supporting information) by comparison with the standard samples. Results showed that the coordination number of Fe-SACs in the Fe-SACs/clusters was 3.09, which indicated that the coordination structure in the Fe-SACs was located at Fe-N3-C. What is more, the strong Fe-Fe bond in the iron-clusters can also be verified as shown in Table S1. As a result, the FT-EXAFS spectra confirmed the existence of both Fe-SACs and iron-clusters in the as-prepared catalysts. In addition, wavelet transform (WT) contour plots of Fe-SACs/clusters showed an intensity maximum located at ~4.7 Å (Fig. 2b). It can be attributed to the Fe-N coordination. In contrast, the WT of standard Fe foils was located at 7.1 Å
The high angle annular dark field scanning TEM (HAADF-STEM) image of Fe-SACs/clusters derived from 1 mol/L of urea-saturated Enteromorpha with microscopic size at 2 nm was given in Fig. 2c. The results showed that the highly dispersed spots with the minority of aggregated spots can be "visualized", which indicated that high amounts of Fe-SACs with scattered iron-clusters were fixed onto the carbon matrixes. The dispersion of Fe-SACs has been significantly improved as compared with that of iron-based catalyst prepared from urea-free Enteromorpha. As shown in Fig. S2, the iron-based catalyst prepared from urea-free Enteromorpha exhibited large aggregated iron-clusters, which confirmed that the 1 mol/L of urea saturation could promote the Fe-N coordination and decrease the Fe-Fe bonds in the urea-saturated Enteromorpha, so as to reduce the existence of iron-clusters. As a result, both XAFS and HAADF-STEM measurements could provide the accurate information on the structure of Fe-SACs/clusters.
The degradation of NPX by Fe-SACs/clusters prepared from 1 mol/L of urea-saturated Enteromorpha, and urea-free Enteromorpha were shown in Figs. 3a and b. The dosage of 0.1 g of Fe-SACs/clusters can achieve 100% of NPX oxidation within 20 min with the kobs of 0.282 min−1. The degradation of NPX was then increased to 0.363 min−1 by adding 0.2 g/L of Fe-SACs/clusters. In contrast, urea-free sample showed less catalytic performance as compared with that of urea-saturated sample; this indicated that the saturation of urea could improve the iron distribution and therefore promote the catalytic performance [17,25]. Comparison of Fe-SACs/clusters with other catalysts for NPX degradation was shown in Fig. 3c and Table S2 (Supporting information). Results showed that the NPX degradation was significantly higher than most reported catalysts and catalytic systems, indicating the exceptional excellent catalytic activity of Fe-SACs/clusters derived from urea-saturated Enteromorpha. In addition, the stability of Fe-SACs/clusters was determined, which showed that after still 95% of catalytic capacity can be maintained after 4 cycles (Fig. S3 in Supporting information).
Quenching tests were conducted to confirm the degradation mechanism in the Fe-SACs/clusters + PMS system. TBA was selected as a HO• scavenger and EtOH was used as probe for both SO4•– and HO• [15,20,22]. As shown in Fig. 4a, the addition of 0.1–0.25 mol/L of TBA and EtOH only showed a very small inhibition on the NPX degradation, with the kobs decreased from 0.282 min−1 to 0.233–0.270 min−1 (Fig. 4b). This result indicated that the radical pathways were not dominated in the catalytic systems. The salt bridge experiment was conducted by putting the PMS and NPX in two separated cells with the Fe-SACs/clusters immobilized onto the graphite electrode, as shown in a galvanic oxidation system (Fig. 4c). A significant current can be observed in the Fe-SACs/clusters immobilized graphite electrode, while no current was shown in the blank graphite electrode (no catalyst was covered). This result indicated that strong electron transfer process was induced by the Fe-SACs/clusters [26].
In addition, open-circuit potential in the Fe-SACs/clusters + PMS system showed a significant increase from 0.3 V to 0.9 V, which was assigned to the formation of Fe-SACs/clusters/PMS* complexes (Fig. 4d). In contrast, no significant open-circuit potential can be observed with the absence of Fe-SACs/clusters [22]. As a result, strong electron transfer process can be induced in the Fe-SACs/clusters + PMS system. This result was consistent with the phenomenon observed in the galvanic oxidation system.
We have deposited the Fe-SACs/clusters onto the ceramic membrane (Fe-SACs/clusters@CM). The Fe-SACs/clusters@CM was prepare by the spraying-crosslinking process [26]. Three steps including spray coating, crosslinking, and annealing at 523 K were involved in the fabrication procedures of Fe-SACs/clusters@CM, as shown in Fig. 5a. The hydrophilic result was determined via a contact angle measurement. Results showed that Fe-SACs/clusters@CM only needed a very short time (< 0.4 s) to fully permeate, which indicated that the as-prepared Fe-SACs/clusters@CM had a very good hydrophilicity (Fig. 5b). In addition, the morphology on the cross-section of the Fe-SACs/clusters@CM was also detected, which showed the well-fixed Fe-SACs/clusters on the surface of CM and their thickness was approximately 30 µm (Fig. 5c).
By feeding the Fe-SACs/clusters@CM with 1 mg/L of NPX and 0.5 mmol/L of PMS, we observed that the NPX can be completely removed and the continuous operation test can be maintained for more than 5 L of solution (Fig. 5d). The dosage of Fe-SACs/clusters onto the CM was small (2.0 mg Fe-SACs/clusters/cm2 of CM), but the well dispersed Fe-SACs/clusters combined with the CM materials could achieve high catalytic performance for the NPX oxidation. This result indicated that the Fe-SACs/clusters@CM could provide a novel strategy for effectively remove the organics in a continuous PMS catalytic system. For future research, the use of the catalyst/CM in a field condition will be important to further evaluate its catalytic activity.
In summary, a high effective iron-based catalyst was prepared from the iron-rich Enteromorpha for NPX degradation. Both Fe-SACs and iron-clusters derived from the intrinsic iron element in Enteromorpha was fabricated after the urea saturation in the Enteromorpha. The electron transfer process was confirmed to be the dominated pathway in the Fe-SACs/clusters + PMS system, while radicals contributed a very minor role for the NPX oxidation. In addition, the depositing of Fe-SACs/clusters onto the CM exhibited a very effective strategy to achieve the continuous NPX degradation in a Fenton-like system.
Declaration of competing interest
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The authors declare that they have no known competing financial interests or personal relationships that could have appeared to influence the work reported in this paper.
Acknowledgments
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The work was supported by National Natural Science Foundation of China (No. 52170086), Shandong Provincial Excellent Youth (No. ZR2022YQ47). The authors also want to thank Conghua Qi from Shiyanjia Lab (www.shiyanjia.com).
Supplementary material
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Supplementary material associated with this article can be found, in the online version, at doi:10.1016/j.cclet.2023.108666.
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Year 2024 volume 35 Issue 3
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doi: 10.1016/j.cclet.2023.108666
  • Receive Date：2023-02-26
  • Online Date：2025-11-21
  • Published：2024-03-15
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  • Received：2023-02-26
  • Revised：2023-05-23
  • Accepted：2023-06-07
Affiliations
    School of Environmental Science and Engineering, Shandong University, Qingdao 266237, China
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表12种不同金属材料的力学参数
科
Family		 属数
Number of
genus		 种数
Number of
species		 占总种数比例
Percentage of
total species (%)		 属
Genus		 种数
Number of
species		 占总种数比例
Percentage of total
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鹅膏菌科Amanitaceae 2 11 5.26 鹅膏菌属 Amanita 10 4.78
小菇科 Mycenaceae 2 12 5.74 丝盖伞属 Inocybe 5 2.39
多孔菌科 Polyporaceae 8 14 6.70 蜡蘑属 Laccaria 5 2.39
红菇科 Russulaceae 3 23 11.00 小皮伞属 Marasmius 6 2.87
小菇属 Mycena 11 5.26
光柄菇属 Pluteus 5 2.39
红菇属 Russula 17 8.13
栓菌属 Trametes 5 2.39
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