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Review

Global Research Trends in Photocatalytic Degradation of Microplastics: A Bibliometric Perspective

Institute for Nanotechnology and Water Sustainability (iNanoWS), College of Science, Engineering and Technology (CSET), University of South Africa (UNISA), Florida, Roodepoort, Johannesburg 1709, South Africa
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Microplastics 2025, 4(3), 35; https://doi.org/10.3390/microplastics4030035
Submission received: 16 March 2025 / Revised: 7 May 2025 / Accepted: 7 June 2025 / Published: 21 June 2025

Abstract

Microplastics have emerged as pervasive contaminants in various ecosystems, raising considerable concerns regarding their impact on environmental health and public safety. The degradation of microplastics is thus recognized as a pressing global challenge. Photocatalytic degradation has emerged as a promising approach due to its potential for efficiency and environmental sustainability. Nevertheless, there remains a need to investigate emerging trends and advancements to understand and fully optimize this technique. Consequently, PRISMA guidelines were employed to define the search parameters, enable the identification of pertinent scholarly articles, and systematically gather bibliographic data from the published literature from 2005 to October 2024. A bibliometric analysis of 204 research articles derived from merged Scopus and Web of Science datasets was conducted to map the field’s research landscape. The analysis showed a robust annual publication growth rate of 17.94%, with leading contributions from China, India, Mexico, and the United Kingdom. Keyword analysis revealed that the commonly applied photocatalysts are titanium dioxide and zinc oxide in the photocatalytic degradation of polyethylene terephthalate, polypropylene, polystyrene, polyvinyl chloride, high-density polyethylene, and low-density polyethylene. Advances in collaboration across Asia and Europe have bolstered the research landscape. However, challenges persist in achieving cost-effective scalability, ensuring the safety of degradation byproducts, and translating laboratory findings into real-world applications. Emerging trends include the development of visible-light-responsive catalysts, advanced nanocomposites, and sustainable photocatalytic technologies. This study underscores the utility of bibliometric tools in identifying knowledge gaps and guiding the development of innovative approaches for microplastic degradation as part of environmental remediation efforts.

1. Introduction

The rise of plastic pollution, particularly microplastics, has become one of the most critical environmental challenges in recent decades. Microplastics, defined as plastic particles less than 5 mm in size, are pervasive across ecosystems, from oceans and rivers to soil and air [1]. Their persistence in the environment is primarily due to the inherent durability of plastic polymers, which resist natural degradation processes. The increasing production of plastics, coupled with their low recycling rates and improper disposal, has led to a global crisis, as microplastics accumulate and pose risks to human health and ecosystems [2,3].
Plastics, such as polypropylene (PP), polyethylene (PE), polystyrene (PS), polyvinyl chloride (PVC), polyethylene terephthalate (PET), polyamide (PA), high-density polyethylene (HDPE), and low-density polyethylene (LDPE), are produced from fossil fuels like petroleum, natural gas, or coal [4]. Despite the environmental problems caused by plastic pollution, their versatility, durability, low cost, and efficiency have made them essential in various industries, including packaging, construction, transportation, electronics, agriculture, healthcare, and sports [5]. However, the widespread use of these plastics has led to significant environmental challenges, particularly the accumulation of microplastics, prompting the search for innovative mitigation strategies [6]. As concerns over microplastic pollution have grown, researchers have explored innovative approaches to mitigate this issue [2].
One such approach is photocatalytic degradation [7,8,9,10], a process that harnesses the power of light and catalysts to break down microplastics into smaller, less harmful substances. Photocatalysis involves the use of semiconductor materials, such as titanium dioxide (TiO2) or zinc oxide (ZnO), which, when activated by light, generate reactive species capable of attacking and degrading plastic polymers [11,12]. This method holds promise as a sustainable and environmentally friendly solution to microplastic pollution, particularly in aquatic environments where microplastics are most prevalent. Unlike traditional waste management techniques, photocatalytic degradation can degrade microplastics in situ, minimizing the need for collection and disposal [13,14].
Photocatalysis is attractive because it utilizes renewable energy sources, such as sunlight, to drive the degradation process. This aspect makes it an attractive solution for reducing the environmental impact of microplastics, particularly in remote or large-scale environments like oceans and lakes where traditional cleanup methods are not feasible. Photocatalysis offers the potential to reduce microplastic particles to their molecular components, ultimately minimizing the risk of further environmental contamination. Additionally, this approach is eco-friendly, as it does not rely on harsh chemicals or energy-intensive processes, aligning with global efforts toward sustainable environmental management [15,16,17].
However, despite the growing body of research on photocatalytic degradation of microplastics, there is a need for a clearer understanding of the global research landscape in this field. Bibliometric analysis is essential for understanding a research field, as it effectively maps the intellectual structure and identifies trends within that domain. Quantitatively analyzing academic publications allows researchers to identify patterns, key contributors, influential papers, and emerging trends. Bibliometrics can uncover hidden connections within a field, providing insights into how research evolves and highlighting areas of high activity or potential gaps in knowledge. This approach is particularly valuable in fast-growing research areas like photocatalytic degradation of microplastics, where keeping track of the vast and diverse literature can be challenging [18,19].
While review papers often summarize recent developments, identify challenges, and propose future research directions, bibliometric analysis takes a systematic, data-driven approach to evaluate global research patterns in specific fields by analyzing literature indexed in academic databases. Initially more familiar within social sciences, library sciences, and informatics, bibliometric analysis has become an increasingly valuable tool across diverse disciplines, allowing researchers to quantify publication trends, map influential authors and institutions, and identify prominent research themes and gaps. Applying bibliometric analysis to the field of photocatalysis provides a fresh methodological perspective, offering insights into dominant research topics, collaboration networks, and evolving research trajectories. This approach highlights current research hotspots and forecasts emerging directions, supporting a comprehensive understanding of the field’s progression and potential future developments [20].
Bibliometric analysis has been significantly enhanced through the development of specialized software tools such as Bibliometrix [21,22], VOSviewer [23,24], and CitNetExplorer [25]. These tools facilitate efficient visualization and comprehensive analysis of bibliographic data, providing researchers with advanced capabilities to map out scientific landscapes. Across numerous disciplines, researchers use bibliometric tools to assess research performance, identify emerging trends, and understand the broader patterns within specific fields of study [26]. For example, Pauna et al. [27] conducted a bibliometric network analysis on the scientific literature concerning microplastics in marine ecosystems. Utilizing VOSviewer, they analyzed keyword co-occurrence, author collaborations, and citation patterns to visualize the research landscape. Kek et al. [28] performed a bibliometric analysis of sustainable strategies for reducing indoor microplastics and converting them into value-added products. The study used data from the Web of Science to map research trends, citation patterns, and collaborations. Zhang et al. [29] reported a study on bibliometric analysis of global trends and prospects in microplastic research. Mehta and Kozielska [30] integrated bibliometric analysis to perform a systematic literature review on sources and analytical approaches of indoor microplastics.
This study utilizes a bibliometric approach to examine global research trends in the photocatalytic degradation of microplastics. By analyzing data from leading scientific databases such as Web of Science and Scopus, we aim to provide a comprehensive overview of the current research landscape, highlighting influential studies, key researchers, and dominant research areas [31]. The Web of Science Core Collection (WoS) and Scopus are leading multidisciplinary databases providing extensive bibliographic information across various research domains. WoS has over 1.9 billion cited references and 85.7 million scholarly records spanning 254 disciplines. At the same time, Scopus offers access to 87 million documents, 1.8 billion citations, and data from 94 thousand affiliations and 7.5 thousand publishers. Independently utilizing WoS and Scopus databases can lead to redundancy and complexity due to overlapping content, making it necessary to eliminate duplicates. It is recommended that metadata be unified for efficient bibliometric research, as each database has unique features [32,33]. Merging both datasets provides comprehensive time coverage, includes new literature, and enhances the accuracy of measuring authors’ impact, thereby improving the analysis of evolutionary citations [19]. User-friendly methods are available—using R packages and Excel—for merging WoS and Scopus datasets while maintaining data integrity [33,34].
Therefore, the primary objective of this study was to conduct a detailed bibliometric analysis of global research on this topic. Specifically, the study seeks to address the following objectives: (1) Identify global research trends by analyzing publication patterns over time to determine periods of rapid growth, the distribution of research efforts across regions, and the evolution of interest in this field. (2) Highlight key contributors by identifying leading countries, institutions, and researchers through co-authorship networks and affiliations, revealing collaboration patterns and geographical expertise concentrations. (3) Evaluate influential publications by identifying the most highly cited studies, journals, and conferences that publish research on this topic, providing insights into impactful works and dissemination channels. (4) Explore emerging trends by analyzing the latest developments to identify new research topics. (5) Identify research gaps by mapping the current research landscape to highlight areas needing further investigation, thereby guiding future research initiatives.

2. Methodology

2.1. Data Source and Search Criteria

Scholarly databases play a pivotal role in bibliometric research and data analysis. Two of the most widely utilized databases are WoS and Scopus, along with others like PubMed and Google Scholar [28]. WoS and Scopus are recognized for their extensive coverage across multiple disciplines. WoS stands out for its broad range of subjects, encompassing science, social sciences, and the humanities [35]. Similarly, Scopus offers comprehensive indexing, particularly strong in scientific, technical, and health-related fields, while covering the social sciences and humanities [19,36]. In addition to their wide-ranging citation data, both databases are valued for their powerful analytical tools, enabling researchers to extract meaningful insights from bibliometric data [37]. Given their reliable indexing, robust coverage, and trusted reputations, this study employed both WoS and Scopus for data mining and analysis, leveraging the strengths of each to ensure a thorough and accurate research process [38].
The Preferred Reporting Items for Systematic Reviews and Meta-Analyses (PRISMA) guidelines [39] were utilized to define the search parameters, identify relevant scholarly articles, and systematically extract bibliographic data from the published literature spanning 2005 to October 2024. The PRISMA 2020 Checklist [40] (Supplementary Materials) informed the search criteria, providing a framework of evidence-based recommendations aimed at enhancing the transparency and thoroughness of systematic reviews and meta-analyses. By adhering to PRISMA standards, the search strategy was designed to ensure replicability and methodological rigor in selecting pertinent publications, thereby strengthening the validity of the review findings. The comprehensive bibliographic data collected played a critical role in evaluating the relevance and contribution of each identified study to the overarching research objective of this analysis.
A search query primarily consisting of (“photocatalytic degradation” OR “photodegradation”) AND (“microplastic*” OR “nanoplastic*” OR “plastic*”) AND (“photocatalyst*” OR catalyst*) was used. The search was performed on 25 October 2024 and was confined to journal articles published in English. The focus was on abstracts, titles, and author’s keywords to ensure relevance. Only primary research articles were considered to ensure the inclusion of original research. Other document types, including review papers, retracted publications, conference proceedings, editorial letters, book chapters, and conference reviews, were intentionally excluded, as they typically synthesize the existing literature rather than presenting new findings [41]. A detailed overview of the data search, selection process, and analysis of the databases is shown in Figure 1. The search before refinement yielded 1623 and 200 documents from WoS and Scopus, respectively, totaling 1823. After refining the search by limiting the publication years and only including original research articles, 1568 documents were obtained from WoS and Scopus. An article was eligible for inclusion in the bibliometric study if it addresses the photodegradation or photocatalytic degradation of PP, PE, PS, PET, PVC, PU, HDPE, and LDPE.

2.2. Merging WoS and Scopus Datasets

The technique used in this study to merge and process data from the WoS and Scopus databases was adapted from the approach outlined by Phiri et al. [18]. An R-script (RStudio 4.2.2) was used to systematically combine WoS plain text files and Scopus bibtex files, as illustrated in Figure 1, integrating both datasets and simultaneously removing duplicate entries. The specific codes used for combining and merging the datasets are provided in the Supplementary Materials. Following the initial data processing, Microsoft Excel was used to analyze Digital Object Identifiers (DOIs) in the resultant Excel file, enabling further refinement by identifying any remaining duplicate records. These steps were essential for excluding duplicates and irrelevant articles that fell outside the scope of this research. As a result, the dataset was refined to focus on research on the photocatalytic degradation of nano/microplastics.

2.3. Data Analysis

Even after exclusions reduced the dataset from 1568 to 1440 entries, the merged dataset still contained entries beyond the study’s scope. A thorough manual screening process was conducted, in which each entry was assessed based on titles, abstracts, and, when necessary, full articles. The focus was explicitly on the photocatalytic degradation of nano/microplastics. Unrelated topics such as thermal degradation of plastics, chemical oxidation processes, mechanical fragmentation of plastics, enzymatic degradation, biodegradation by microorganisms, and recycling of plastics (mechanical or chemical) were excluded. Excluding the articles with these topics was necessary to maintain a focused and high-quality dataset for bibliometric analysis. Hence, this careful curation narrowed the dataset from 1440 to 204 entries (see Supplementary Materials), ensuring relevance for the intended analysis [19].
To maintain a strong focus on the study’s objectives, researchers carefully refined the dataset, enabling a more precise and insightful analysis of trends within the field. The dataset was meticulously reviewed and validated in its final Excel format before initiating the bibliometric analysis, ensuring the accuracy, completeness, and integrity of the data uploaded for examination [34]. A comprehensive science mapping analysis was then performed using Bibliometrix (version 4.1.3), a robust R-tool developed by Aria and Cuccurullo [21]. For visualization purposes, Biblioshiny, the web-based interface of Bibliometrix, was employed to create graphical representations of the analyzed data.

3. Results and Discussion

3.1. Advancements in Research Interests and Publication Output

Table 1 presents a summary of key primary information deciphered by Bibliometrix. It highlights key bibliometric metrics such as the annual growth rate, the analyzed period’s duration, the total number of documents included, and the primary sources contributing to the dataset.
The bibliometric analysis of photocatalytic degradation of microplastics and nanoplastics reveals a growing research interest in this field over the past two decades (2005–2024). The 17.94% annual growth rate highlights the accelerating pace of scientific contributions driven by increasing environmental concerns. A total of 204 articles from 112 sources were analyzed, with an average of 31.75 citations per document, indicating a strong impact and relevance of the research. The field exhibits a high level of collaboration, with an average of 5.42 co-authors per document and 25.98% international co-authorships, reflecting a global research effort. The document average age of 5.91 years suggests this is a relatively young yet rapidly evolving field. The analysis also highlights an extensive knowledge network, with 624 Keywords Plus (ID) and 522 Author’s Keywords (DE), demonstrating the multidisciplinary nature of research in photocatalytic degradation of plastic pollutants. However, the presence of only two single-authored documents suggests that individual contributions are rare, emphasizing the collaborative nature of this research domain. The bibliometric trends indicate a dynamic and expanding scientific landscape, underscoring the urgent need for sustainable microplastic and nanoplastic pollution solutions.
Industries discharge substantial quantities of wastewater into lakes and rivers, resulting in significant environmental pollution [42]. Traditional water treatment methods often need to catch up regarding long reaction time, efficiency, and cost-effectiveness [43]. In recent years, photocatalysis has emerged as a promising alternative for wastewater treatment. This method is particularly appealing due to its effectiveness in degrading pollutants through redox reactions and its ability to utilize sunlight, an abundant and free energy source [44]. Consequently, there has been a notable increase in research and publications focusing on photocatalytic wastewater treatment. Photocatalysis has been explored as an effective method for removing microplastics from water. This advanced treatment process can be integrated as a tertiary stage in wastewater treatment plants, enhancing their ability to address microplastic pollution. During photocatalysis, microplastics undergo degradation, breaking down into carbon dioxide and water or converting into molecular species that are generally less toxic. This finding makes photocatalysis a promising option for mitigating the environmental impact of microplastics in wastewater treatment [7].
In addition, the United Nations Sustainable Development Goals (SDGs), particularly Goal 6, which targets access to clean water and sanitation for all by 2030, have sparked considerable interest and engagement within the research community [45]. The urgency of addressing global water scarcity and pollution, coupled with the need for sustainable management of water resources, has motivated scholars to focus on developing innovative and environmentally sustainable solutions for water treatment. These goals highlight the importance of tackling the adverse effects of water contamination, including emerging pollutants such as microplastics, and emphasize adopting economically feasible technologies that minimize environmental impact. Consequently, the SDGs have become a driving force for research initiatives to advance water purification methods that are effective and sustainable long-term, aligning with global efforts to safeguard water resources for future generations [19].
The earliest photocatalysts identified were wide bandgap semiconductors [46]. While these materials are effective, they have significant limitations, primarily their ability to absorb light only in the ultraviolet spectrum, which restricts their photocatalytic efficiency. It is important to note that solar energy contains only about 3–5% UV radiation, while visible light constitutes approximately 43% of solar energy. This observation implies that a considerable portion of solar radiation remains untapped. Considering this, there is an increasing focus on developing visible-light-driven narrow bandgap semiconductors that can effectively absorb light in the visible spectrum, thereby enhancing photocatalytic activity and utilization of solar energy [20,47].

3.2. Overview of Photocatalysts for Nano- and Microplastic Degradation

Table 2 summarizes recent studies on photocatalysts for degrading different nano- and microplastics. It lists the photocatalyst types, synthesis methods, targeted plastics, irradiation sources, reaction times, and degradation efficiencies, highlighting diverse approaches and their potential for sustainable plastic degradation.
Photocatalytic degradation of nano- and microplastics under UV, sunlight, and visible light have been explored in multiple studies employing various advanced photocatalysts [7,8,9,10,46,47,48,49,50,51,52,53,54,55,56], with distinct mechanisms and material-specific properties aimed at mitigating plastic pollution effectively. Table 2 provides a comprehensive summary of photocatalysts used in these studies. The bio-inspired C,N-TiO2/SiO2 photocatalyst synthesized using extrapallial fluid from Mytilus galloprovincialis for PET degradation under visible light exemplifies innovation in materials design. The catalyst’s high surface area and suitable bandgap energies enabled degradation efficiencies ranging from 9.35% to 16.22% after 120 h, particularly under acidic conditions (pH 6). The degradation process was confirmed using structural and thermal analyses, revealing significant changes in PET properties and surface morphology (Figure 2a,b), with enhanced activity attributed to synergistic carbon and nitrogen doping [7].
Similarly, CuO/BiVO4 nanocomposites were explored for degrading LDPE, PP, and PA via an enhanced photo-Fenton process. The formation of a p–n heterojunction between CuO and BiVO4 enhanced charge transfer and promoted the generation of reactive oxygen species (ROS). This facilitated efficient oxidation processes, leading to effective polymer breakdown, as demonstrated by the increased carbonyl and vinyl indices (Figure 2c–e). However, the treated water showed some toxicity, highlighting the necessity for dilution before discharge [8]. Another notable system reported by Qi et al. [9] is Ni2P/TiO2/C nanofibers (NFs). This system achieved efficient charge separation and reduced electron–hole recombination during PET degradation under visible light, with KOH pretreatment further enhancing degradation performance [9]. In the case of BiOCl-ZrO2, degradation of LDPE under visible light resulted in a 48.67% weight reduction over 24 days, with a type-II heterojunction improving charge separation and reducing recombination. The process, however, had a measurable carbon footprint, emphasizing the need for further optimization to align with sustainable development goals [10].
Studies have also explored the use of Fe3O4 particles and composites, such as Fe3O4/g-C3N4, which leverage magnetic properties for easy separation and redox cycling to generate radicals under UV-A light, achieving PET degradation rates up to 40% in 8 days [49]. A Z-scheme photocatalyst, g-C3N4/WO3, demonstrated efficient PET degradation and hydrogen production under visible light, with enhanced ROS formation facilitating the breakdown of polymer chains [50]. BiOCl nanostructures were tested for PS degradation, where BiOCl nanodisks achieved superior performance compared to nanoflowers due to efficient ROS generation. This is evidenced by surface roughness (Figure 2f) and cavity formation (Figure 2g) [51]. A composite of TiO2-polyaniline (PANI) demonstrated an enhanced charge separation due to strong TiO2-PANI interactions leading to improved chain scission and photo-oxidation. The composite also showed significant weight loss of PS due to volatile gas formation during degradation, offering a practical approach for PS waste treatment [52].
Innovative photocatalysts such as graphene oxide-zinc oxide (GO-ZnO) composites and ZnO nanoparticles (ZnO NPs) have shown promise for LDPE and sewage-derived plastics degradation, respectively. GO-ZnO achieved a 39.47% mass loss of LDPE under UV light in just 2 h due to improved charge separation, while ZnO NPs demonstrated effective degradation of various polymers, including PE, PP, PVC, and PET, as confirmed by Raman and FTIR spectra [53,54]. Additionally, C,N-TiO2 achieved 71.77% degradation efficiency of HDPE under visible light in 50 h, with enhanced activity attributed to hydroperoxide formation and increased MP surface area through fragmentation [48].
Soil-mediated photocatalytic degradation using components like clay, iron oxides, and MnO2 highlighted the critical role of environmental catalysts in enhancing polymer breakdown. The interplay between MPs and soil components, particularly clay minerals and iron oxides, facilitated degradation through electrostatic interactions, as confirmed by SEM and ATR-FTIR analyses (Figure 2h–j) [55,56]. Moreover, advanced composites like CuO/Bi2O3/g-C3N4 achieved 41.60% degradation of PET MPs under sunlight. Similarly, photodegradable PVC films with nano-graphite and TiO2 showed a 17.24% weight loss under UV irradiation. SEM images revealed surface porosity and a honeycomb-like structure (Figure 2k), demonstrating promising degradation performance through enhanced charge separation and ROS generation [57,58].

3.3. Document Types and Quantities

In this study, 1823 records related to microplastic research were retrieved. In the beginning, the statistical data of the studies were sorted and analyzed to draw preliminary conclusions on research trends. The documents were classified into seven distinct categories (Figure 3a), with the largest share being original research articles, accounting for 86.5% of all publications. Review articles and proceeding papers accounted for 5.3% and 5.8%, respectively. Early access (1.3%), book chapters (0.9%), editorial letters (0.1%), and retracted publications (0.1%) were among the less significant categories. The predominance of original research articles is a key indicator of growth and evolution within microplastic research. Therefore, the analysis focused primarily on original research articles on the photocatalytic degradation of nano/microplastics to better capture trends, advancements, and knowledge gaps in the field. This focus enables a detailed evaluation of the core literature shaping the direction of microplastic research.
The annual production of articles and citation data in Figure 3b and Table S1 (Supplementary Materials) highlights important trends regarding the progression, impact, and development of research in photocatalytic degradation of nano/microplastics. From 2005 to 2014, scientific production was relatively low and fluctuated moderately, with publication numbers ranging between 1 and 11 per year. However, after 2018, there was a noticeable increase in publications, marking a sharp rise in 2021. This upward trend peaked in 2023 with 37 publications, indicating a growing research interest. Although there was a slight decrease in 2024 to 23 publications (please note that by 25 October 2024, only 81.69% of the year is considered), the overall trend suggests heightened awareness and increased research activity over recent years. The problem of nano/microplastics has become a prominent environmental concern, driving heightened academic and research interest. This rise likely reflects increased awareness of microplastic pollution’s ecological and health risks, leading to more funding and a greater focus on finding effective mitigation solutions [28,59].
The mean total citation per year reveals fluctuating impact over time. Initially, between 2005 and 2013, the average citations were relatively low and inconsistent. A significant increase in citations began in 2019, reaching a peak of 13.11 and 12.62 citations per year in 2020 and 2021, respectively. These peaks may reflect highly influential studies or growing recognition within the field. However, the mean citation rate has declined recently, with 2024 averaging only 2.22 citations per paper, likely due to the shorter period for citations to accumulate. This trend suggests both growing research interest and variation in the immediate impact of recent studies.
The trend in publication volume does not usually align with the average citation pattern. It is common to experience a delay between when a document is published and when it begins to receive citations. This delay is known as citation lag [60]. Such a lag arises because newly published research requires time to be discovered, read, and cited by other scholars in their subsequent works. As a result, even in fields where the number of publications is increasing, indicating a positive growth trend, the citation counts for more recent articles tend to be lower than those for older publications. This phenomenon occurs because the research community needs time to absorb and integrate new findings into their work, which is then reflected in citation records [61]. This phenomenon is a normal aspect of the scholarly communication process and highlights the iterative nature of research and the dissemination of knowledge. It underscores the fact that while publication rates may rise, citation practices often lag, reflecting the gradual process through which new information gains recognition and influence within the academic community [19].

3.4. Source Dynamic Production

Figure 4 shows leading journals and cumulative journal production over time. As shown in Figure 4a, Polymer Degradation and Stability stands out as the leading journal with 23 articles on this topic, reflecting its focus on materials degradation, particularly polymers, which aligns well with the study of plastic breakdown in environmental contexts. The Journal of Hazardous Materials follows with 12 articles, emphasizing the hazardous nature of micro- and nanoplastics and the importance of developing effective degradation strategies to mitigate their environmental impact. The Journal of Environmental Chemical Engineering and Journal of Applied Polymer Science also have significant contributions, with 10 and 9 articles, respectively. These journals cover areas relevant to the environmental chemistry of degradation processes and the engineering challenges associated with using photocatalytic materials to address plastic pollution.
Figure 4b shows the growth in publication output over time for each journal, revealing trends in scientific attention toward photocatalytic degradation of plastics. Polymer Degradation and Stability has steadily increased in publications since 2006, leading the field and likely reflecting ongoing advancements in understanding polymer stability and breakdown. The Journal of Hazardous Materials began contributing significantly in 2008 and has recently increased awareness of the environmental hazards associated with micro- and nanoplastics. The Journal of Environmental Chemical Engineering saw a sharp increase starting around 2019, suggesting recent developments in applying chemical engineering principles to this environmental challenge.
Table 3 provides metrics for the journals, such as the h-index, g-index, m-index, total citations (TC), number of publications (NP), and the year of publication start (PY_start). For example, Polymer Degradation and Stability has an h-index of 15 and a g-index of 23, indicating both the productivity and impact of its publications in this field. Meanwhile, the Journal of Hazardous Materials has a higher total citation count (1072) despite a lower number of publications, suggesting that its articles are highly influential, possibly due to their focus on addressing hazardous aspects of plastic pollution. Journals like the Chemical Engineering Journal and the Environmental Science & Technology are recent but impactful contributors in this field, showing high m-index values and rapid citation accumulation, indicating that newer publications garner attention and may be pivotal in advancing photocatalytic degradation techniques.

3.5. Three Field Plot

The three-panel plot in Figure 5, also known as the tripartite Sankey Diagram, provides a comprehensive visualization of the relationships among authors, authors’ keywords, and journals (sources) in the photocatalytic degradation of the microplastics research field. The three-panel visualization illustrates the interconnections among research keywords, influential authors, and key publication sources in this research field. The keywords panel shows the core concepts being studied, such as photocatalysis, degradation, photodegradation, polyethylene terephthalates, polyethylene, microplastics, and polystyrene. The density and interconnections between these keywords suggest they are closely related and central to the research. The author’s panel identifies the key researchers contributing to this work. Prominent authors such as Wang H, Cedillo-González E, Zan I, and Chakrabarti S emerge as key contributors, reflecting their impactful publications and significant collaborative efforts in the field. The sources (journals) field reveals the top publication outlets for this research, including the Journal of Hazardous Materials, Journal of Applied Polymer Science, and Polymer Degradation and Stability. The thick connections between specific journals suggest they are frequently cited together, reflecting their topical relevance.

3.6. Leading Authors, Institutions, and Countries

A comprehensive analysis of photocatalytic degradation of microplastics research is provided in Figure 6 and Table S2 (Supplementary Materials). Seven hundred and ninety-four authors have contributed to the field, notably in Asia and Europe. Figure 6a ranks authors by article count, with Wang H and Cedillo-González E leading with 11 and 9 articles, respectively. This observation aligns with the data provided in Table 4, where both authors also have high h-indices (8), suggesting that their work has garnered substantial recognition and citations over time. However, other authors in Figure 6a with similar article counts, such as Zan L, Deng K, and Fa W, show varied h-indices, g-indices, and total citations (TCs) in the table. These results indicate that while they have produced comparable quantities of articles, the impact and citation frequency differ across individuals.
Table 4 also provides insights into when each author started publishing in this field (PY_start), which can explain some of the trends in Figure 6a. For instance, authors like Zan L and Deng K, who began publishing in 2006, have had more time to accumulate articles, possibly contributing to their presence in Figure 6a. In contrast, Cedillo-González E, who only started publishing in 2019, has achieved a comparable article count in a shorter timeframe, further highlighted by a high m-index of 1.333 (Table 4). This m-index, representing the h-index normalized by years since the first publication, suggests a rapidly growing impact for newer researchers.
Additionally, some authors have higher g-indices and total citations despite fewer articles, as seen with Siligardi C and Hernández-López J, indicating their work may be particularly influential or widely cited. Therefore, while Figure 6a illustrates publication quantity, Table 4 provides a broader perspective on each author’s research impact, publication timeline, and citation metrics. The article count alone does not fully capture the academic influence of these authors. The impact metrics from Table 3 complement Figure 6a by revealing the quality and influence behind the publication numbers.
Figure 6b presents the top institutions involved in this field, with Universidad Autonoma de Nuevo Leon (UANL, Mexico) contributing the highest number of publications (20), followed by University of Calcutta (CU, India) and Universita Di Modena E Reggio Emilia (UNIMORE, Italy). This concentration of publications in specific institutions suggests that these centers have dedicated resources and facilities for advancing environmental remediation techniques. Institutional leadership like this is important because it fosters collaboration with industry and governmental organizations, potentially facilitating the translation of research findings into practical technologies for wastewater treatment. These high-output institutions can drive technological advances and influence global research priorities in addressing plastic pollution [62].
As illustrated in Figure 6c, China produced the highest volume of publications of 85 articles, representing 41.7% of the total output. India follows with 22 articles (10.8%), then Mexico (15 articles, 7.4%), the United Kingdom (12 articles, 5.9%), and Japan (8 articles, 3.9%). Meanwhile, contributions from India and Mexico reflect a rising interest in addressing microplastic contamination in diverse regions, highlighting an emerging awareness and prioritization of environmental sustainability in developing countries. This trend aligns with global research funding shifts and environmental policies emphasizing sustainable technologies and pollution management.
Figure 6d distinguishes between single-country publications (SCPs) and multi-country publications (MCPs), revealing collaboration patterns. China’s high SCP rate indicates strong domestic research capacity, while countries such as Italy and Iran show higher MCP rates, emphasizing international collaboration to leverage diverse expertise. This collaborative trend is particularly valuable in photocatalysis, where interdisciplinary knowledge in materials science, environmental science, and engineering is necessary to develop practical solutions for microplastic degradation. International partnerships can foster innovation through shared resources, enabling more comprehensive research outcomes and optimizing photocatalytic applications across different environmental contexts. The partnerships align with research growth, suggesting that countries with fewer resources benefit significantly from international collaboration in specialized fields, allowing for broader adaptation and implementation of technology solutions [63].
The publication output from various academic affiliations over time is illustrated in Figure 7. From the figure, a notable increase in research activity since around 2015 is observed. Universidad Autónoma de Nuevo León (UANL, Mexico) demonstrates the most significant growth, particularly after 2018, which suggests an intensified focus on this research area in recent years. In contrast, the University of Calcutta (CU, India) and Wuhan University (WHU, China) show steady outputs, reflecting consistent contributions over time but with less rapid recent growth than Universidad Autónoma de Nuevo León. South Central Minzu University (SCMU, China) began contributing earlier and maintained a relatively stable publication rate, indicating an early and sustained interest.
Additionally, Università di Modena e Reggio Emilia (UNIMORE, Italy) and the National Institute of Technology (NIT, India) show moderate contributions, with more gradual increases in their publication output. These trends reflect the growing global attention to environmental sustainability and pollution, particularly concerning micro- and nanoplastics. The trend in the figure suggests that institutions from diverse regions are increasingly prioritizing research on photocatalytic degradation to address the environmental challenges associated with plastic pollution.

3.7. Journal Co-Citation Analysis

Analyzing the most cited articles provides insight into the key studies driving research in photocatalytic degradation of microplastics. This information shown in Table 5 is valuable for understanding foundational and influential works and identifying impactful authors and trends within the field. The highest-cited paper, authored by Tofa et al. in 2019 [64] and published in Environmental Chemistry Letters, has accumulated 278 citations, with an average of 46.33 citations per year and a normalized citation count of 4.35. Following this, Uheida’s 2021 [65] study in the Journal of Hazardous Materials has received 273 citations, showing strong yearly growth with 68.25 citations per year and a high normalized citation count of 5.41, indicating a significant recent impact.
Table 4 highlights the Journal of Hazardous Materials as a key outlet, featuring multiple influential papers, such as Ariza-Tarazona’s studies from 2020 [48] and 2019 [66], with 238 and 210 citations, respectively. This journal serves as a core source for advancements in photocatalytic degradation, contributing extensively to the research on this topic. Other impactful journals include Polymer, where Zhao’s 2006 article [67] garnered 232 citations, and iScience, with Nabi’s 2020 [68] publication receiving 193 citations and a robust annual citation rate of 38.60. The reported data reveals a mix of older foundational studies and recent publications with rapidly growing influence. Notably, work by Cao and colleagues [69] in the Journal of Colloid and Interface Science has already amassed 122 citations at an impressive rate of 40.67 per year, signifying the ongoing relevance and dynamic interest in recent research contributions. These highly cited articles underscore key studies and journals that have shaped the field of photocatalytic degradation of microplastics, indicating both established and emerging research trajectories.
Table 5. Summary of most cited articles on photocatalytic degradation of nano/microplastics.
Table 5. Summary of most cited articles on photocatalytic degradation of nano/microplastics.
AuthorsJournalTCTC/YearNormalized TC
Tofa T et al., 2019 [64]Environ Chem Lett27846.334.35
Uheida A et al., 2021 [65]J Hazard Mater27368.255.41
Ariza-Tarazona M et al., 2020 [48]J Hazard Mater23847.603.63
Zhao H, 2006 [67]Polymer23212.212.78
Ariza-Tarazona M, 2019 [66]Ceram Int21035.003.29
Nabi I, 2020 [68]iScience19338.602.94
Zhao X, 2007 [70]J Mol Catal A Chem18210.111.64
Jiang R, 2021 [71]J Hazard Mater16842.003.33
Tofa T, 2019 [72]Catalysts13322.172.08
Zan L, 2006 [73]Environ Sci Technol1226.421.46
Cao B, 2022 [69]J Colloid Interface Sci12240.674.39
Llorente-García B, 2020 [74]Coatings10420.801.59
Liang W, 2013 [75]Polym Degrad Stab1028.502.16
Domínguez-Jaimes L, 2021 [76]J Hazard Mater10025.001.98
Zhao X, 2008 [77]Appl Surf Sci975.711.93
Chakrabarti S, 2008 [78]J Hazard Mater915.351.81
Zhou D, 2022 [79]Adv Fiber Mater9030.003.24
Fernando S, 2007 [80]Polym Degrad Stab854.720.77
Zan L, 2006 [81]Polymer844.421.01
Thomas R, 2013 [82]Colloids Surf A786.501.65
TC = Total citations.

3.8. Keyword Analysis

The density visualization map (Figure 8) and keyword co-occurrence network (Figure 9a) provide a comprehensive bibliometric perspective on research trends in the photocatalytic degradation of nano/microplastics in aquatic environments. They both reveal a well-defined research landscape, with “photocatalytic degradation” emerging as the central theme, exhibiting strong linkages with key terms such as “microplastics,” “photocatalyst,” “ZnO,” and “UV radiation.” This observation indicates that significant efforts have been directed toward utilizing semiconductor-based photocatalysis, particularly ZnO-driven processes under UV light, to degrade microplastics in aquatic systems. The presence of widely studied polymer types, including “polyethylene terephthalate,” “polystyrene,” “polyvinyl chloride,” and “polypropylene,” highlights the breadth of research focusing on understanding degradation pathways for different plastic pollutants. Additionally, the frequent co-occurrence of “wastewater” and “plastic pollution” suggests that photocatalytic degradation is not only explored as a fundamental process but also increasingly regarded as a viable solution for tackling microplastic contamination in real-world water treatment applications.
The overlay map (Figure 9b) provides further insights into the evolution of research trends over time. Keywords represented in warmer colors, such as “visible light photodegradation,” “advanced oxidation processes,” and “peroxymonosulfate activation,” indicate a growing shift toward more efficient and sustainable photocatalytic systems that operate under visible light conditions. This transition aligns with the increasing global focus on developing photocatalysts capable of harnessing solar energy, thereby overcoming the limitations of conventional UV-driven processes. The co-occurrence of terms such as “kinetic model” and “reaction mechanism” in more recent studies further suggests a rising emphasis on understanding the fundamental kinetics and mechanistic pathways of photocatalytic degradation. This focus is essential for optimizing process parameters and scaling up these technologies for practical environmental applications.
The clustering of keywords also reveals distinct research subdomains. One primary cluster revolves around the degradation behavior of various polymers, as evidenced by terms like “polyethylene film” and “low-density polyethylene,” indicating studies dedicated to assessing the susceptibility of different microplastic types to photocatalytic processes. Another cluster is centered on advanced photocatalytic strategies, including “nanotechnology,” “doping,” and “grafting,” highlighting the ongoing pursuit of engineered photocatalysts with enhanced efficiency. Furthermore, the presence of “wastewater,” “recycling,” and “mechanical properties” signifies the practical implications of photocatalytic degradation in water purification and circular economy approaches.
The bibliometric analysis provides valuable insights into well-established research areas, emerging trends, and potential knowledge gaps in nano/microplastic photocatalytic degradation. The increasing research focus on visible-light-driven photocatalysis, advanced oxidation techniques, and mechanistic studies suggests a promising trajectory toward developing more effective and scalable solutions for plastic pollution remediation. However, critical challenges remain, including enhancing the long-term stability of photocatalysts, improving degradation efficiency under natural sunlight, and understanding the environmental fate of transformation products.
Future research should emphasize integrating these technologies into real-world applications, optimizing reaction kinetics for large-scale deployment, and assessing the ecological risks of degradation byproducts. Addressing these challenges will be pivotal in bridging the gap between laboratory-scale studies and practical environmental solutions for microplastic pollution.

3.9. Global Collaboration Network

Figure 10 illustrates the global collaboration network on photocatalytic degradation of nano/microplastics, revealing the interconnected research efforts to address plastic pollution through advanced photocatalytic processes. Photocatalytic degradation leverages photocatalysts like TiO2, ZnO, TiO2–P25/β-SiC, Ag/TiO2, Nb2O5, and TiO2-rGO. When these photocatalysts are exposed to light, they generate reactive oxygen species capable of breaking down plastic polymers into less harmful compounds, addressing the persistent issue of micro- and nanoplastics in water systems [14].
The map shows China as a dominant player, frequently collaborating with nations like the USA, Korea, and the United Kingdom, indicating its strong research infrastructure and investment in environmental technologies. The People’s Republic of China’s partnerships with the USA and Korea are the most frequent, each recorded four times, emphasizing a shared interest in advancing photocatalytic methods to mitigate plastic pollution. European countries such as Germany, Spain, and the UK also exhibit strong research ties, often forming intra-European collaborations (e.g., Germany–Spain) and connecting with non-European countries (e.g., Germany–China and UK–USA). These collaborations are essential for pooling resources, technology, and expertise to refine photocatalysts, enhance degradation efficiency, and address challenges like scalability and environmental application.
For instance, the USA’s collaborations with Iran and Saudi Arabia might focus on adapting photocatalytic methods for regions with high solar irradiance, leveraging sunlight as a cost-effective catalyst activator. Similarly, partnerships between China and Japan likely aim to innovate in catalyst design and nanoparticle engineering, enhancing degradation rates of polyethylene and polypropylene, common microplastic pollutants. Collaborations within Asia, such as between Korea and Vietnam, reflect growing regional interest in addressing plastic waste locally through photocatalytic technology. The collaboration frequencies and patterns highlight the global scientific community’s response to the urgent issue of microplastic pollution. Through such networks, researchers can accelerate the development of photocatalysts, optimize degradation processes, and explore application potentials, ultimately aiming for large-scale environmental remediation solutions.
Figure 11 represents the author collaboration network and collaboration density shown in Figure S2 (Supplementary Materials). Each node in the network denotes an author, and each node’s size indicates the author’s influence or productivity in this research area. The connections (or edges) between nodes show collaborative relationships, with clusters of nodes representing groups of authors who frequently co-author papers. The red cluster, with prominent authors like Wang H, Liu X, and Liu J, appears to be the most active group in this research area, suggesting that this team has a significant number of publications or substantial influence in the study of photocatalytic degradation. The density of connections within this cluster indicates strong internal collaboration involving the development of innovative photocatalysts or studying the degradation mechanisms of various plastics under photocatalytic processes.
The green cluster, featuring authors like Deng K, Fa W, and Zan L, is another active collaboration network, though smaller and slightly less connected than the red cluster. This group may focus on complementary aspects of photocatalytic degradation, such as optimizing catalyst structures or exploring different environmental applications. The connections between the green and red clusters suggest occasional collaboration between these groups, sharing findings or jointly investigating specific degradation methods. Other clusters, such as those in purple, gray, and brown, represent smaller, more isolated research groups that are less integrated into the main networks. These authors might be exploring niche areas within photocatalytic degradation, such as specific types of nano/microplastics or specialized catalysts. For instance, the purple cluster led by Nakatani H could be working on particular photocatalytic reactions or materials that differ from the primary focus of the larger clusters.
The relatively isolated authors, like Dong X and Luo X (orange cluster), may represent individual contributors or smaller teams with unique research directions or methodologies. Although their work may need to be more highly integrated into the more extensive networks, they could offer valuable insights or alternative perspectives within the field. These clusters’ spread and interaction patterns reflect the interdisciplinary nature of research on photocatalytic degradation of nano/microplastics. The interconnectedness of the primary clusters highlights the importance of collaboration in advancing knowledge on degradation mechanisms, catalyst efficiency, and environmental applications. In contrast, smaller and isolated clusters bring diversity to the field, pushing the boundaries of current understanding and potentially introducing novel approaches.

3.10. Trending Topics

Figure 12 presents a bubble chart depicting trending research topics in the field of photocatalytic degradation of nano/microplastics, offering a comprehensive overview of key themes related to materials, processes, and applications. The size of each bubble represents the relative research activity or prominence of a given keyword within a defined timeframe, providing a clear, data-driven visualization of the evolution of both emerging and well-established areas of interest. This analytical framework identifies shifts in research focus, distinguishing rapidly expanding fields from long-standing domains that continue to attract substantial scientific attention.
The chart reveals that growing environmental concerns, particularly microplastic pollution and plastic waste accumulation, have been primary drivers of research in photocatalytic degradation. Notably, “photocatalysis” and “photocatalytic degradation” have exhibited consistent research momentum since approximately 2010, underscoring the increasing recognition of plastic pollution as an environmental crisis and the urgent need for scalable, sustainable remediation technologies. Photocatalysis, which harnesses solar or artificial light to degrade organic pollutants, aligns closely with global trends promoting green and sustainable technologies [83]. The expanding research focus on photocatalytic solutions highlights their potential for tackling persistent plastic pollution and advancing eco-friendly degradation strategies, reinforcing the role of photocatalysis as a cornerstone of next-generation environmental remediation.
A surge in research on microplastics since 2017 parallels increased recognition of their environmental impact, persistence in ecosystems, and threats to aquatic life and human health [14]. Photocatalysis offers a promising solution for targeting microplastic pollutants that resist conventional treatment techniques. Additionally, common polymers such as “polyethylene terephthalate,” “low-density polyethylene,” “polypropylene,” and “polyvinyl chloride” have seen a rise in research interest since around 2015. These materials are prevalent in packaging and contribute significantly to plastic waste, necessitating innovative breakdown techniques. Photocatalytic methods hold the potential for degrading these persistent polymers, providing an environmentally friendly solution to plastic pollution [14].
Zinc oxide and titanium dioxide stand out as popular photocatalysts. Research on TiO2 has been active for years due to its stability, non-toxicity, and high efficiency. At the same time, interest in ZnO has grown more recently as it presents an alternative or complementary photocatalyst with the potential for visible-light applications, enhancing energy efficiency [81]. Advances in “nanocomposites” highlight innovations in nanotechnology and materials science; these materials combine photocatalysts with other nanomaterials to improve properties like surface area and degradation efficiency.
The prevalence of studies involving “sunlight” from 2018 indicates an increased interest in using natural solar energy for photocatalytic processes, aligning with global sustainability goals. Sunlight-driven photocatalysis offers a cost-effective and eco-friendly approach, ideal for large-scale environmental remediation projects. These trends underscore the importance of sustainable environmental technologies to tackle issues like plastic pollution. Innovations in photocatalytic materials, particularly in nanocomposites and visible-light-active catalysts, are expected to drive future advancements. Utilizing renewable energy sources like sunlight may enable photocatalytic degradation to become a viable large-scale solution for breaking down microplastics and other pollutants, reducing dependency on fossil fuel-based treatments, and minimizing ecological impacts.

3.11. Research Gaps and Future Directions

Despite advancements in photocatalytic nano/microplastic degradation, critical gaps persist, limiting practical scalability. A key challenge lies in the understudied degradation mechanisms of environmentally prevalent yet overlooked polymers, such as polystyrene copolymers, high-impact plastics, and biodegradable materials. While these constitute a substantial fraction of plastic waste, their reaction kinetics, pathways, and photocatalytic efficiencies remain poorly characterized, hindering the development of tailored solutions. Equally limiting is the narrow focus on conventional photocatalysts like TiO2 and ZnO, despite the promise of alternatives such as bismuth-based compounds (BiOCl, BiVO4), tungsten oxides (WO3/g-C3N4), and hybrid nanocomposites (CuO/BiVO4, graphene oxide hybrids). These materials exhibit superior visible-light absorption and charge separation but require systematic exploration to unlock their potential for real-world applications. Scalability further complicates progress: while lab-scale studies report promising results under controlled UV/simulated sunlight, performance under natural conditions, with variable light intensity and environmental factors, is rarely validated. Extended degradation times (e.g., 175 h for ZnO, 20 days for soil-integrated systems) underscore inefficiencies that demand optimization through kinetic modeling, reactor engineering, and solar-responsive catalyst design.
Another critical gap is the insufficient analysis of degradation byproducts. Many studies prioritize efficiency metrics over identifying intermediates or assessing their ecotoxicity, particularly for widely used TiO2 and ZnO systems. Comprehensive profiling using advanced techniques (e.g., high-resolution mass spectrometry, chromatography) is essential to ensure environmental safety and regulatory compliance. Additionally, research disproportionately targets monolithic polymers (PET, LDPE, HDPE), neglecting complex materials like multilayer composites, polymer blends, and additive-containing microplastics, whose distinct properties may alter degradation kinetics. Addressing these gaps necessitates interdisciplinary collaboration to bridge materials science, environmental chemistry, and engineering. Future efforts must prioritize (1) diversifying photocatalysts toward visible-light-active and hybrid systems, (2) expanding polymer coverage to include emerging and complex plastics, (3) optimizing kinetics for faster degradation under ambient conditions, (4) implementing rigorous byproduct characterization, and (5) performing pilot-scale reactor validations. By integrating these approaches, photocatalytic degradation can evolve into a scalable, sustainable tool for mitigating global nano/microplastic pollution.

4. Conclusions

The photocatalytic degradation of nano/microplastics has emerged as a promising and sustainable approach for mitigating plastic pollution, offering significant potential for environmental remediation. This bibliometric analysis, based on 204 research articles published between 2005 and October 2024, has comprehensively evaluated global research trends, key contributors, influential publications, and emerging research directions in this domain. The field has exhibited a robust annual growth rate of 17.94%, with significant contributions from China, India, Mexico, and the United Kingdom, reflecting the increasing global attention to microplastic pollution and sustainable degradation technologies.
Keyword analysis revealed that titanium dioxide (TiO2) and zinc oxide (ZnO) remain the most widely studied photocatalysts, primarily applied to degrade polyethylene terephthalate (PET), polypropylene (PP), polystyrene (PS), polyvinyl chloride (PVC), high-density polyethylene (HDPE), and low-density polyethylene (LDPE). However, recent trends indicate a growing focus on visible-light-responsive photocatalysts, advanced nanocomposites, and hybrid materials, which have the potential to overcome the limitations of UV-dependent degradation processes and enhance degradation efficiency under ambient environmental conditions.
Despite these advancements, several critical research gaps remain. Limited studies have explored the degradation pathways of complex plastic composites, co-polymers, and emerging biodegradable materials, which are increasingly prevalent in commercial applications and environmental waste streams. Additionally, while significant progress has been made in developing novel photocatalysts, the scalability and real-world applicability of these technologies remain a considerable challenge. Many reported systems exhibit long reaction times, limited efficiency under natural light conditions, and uncertainties regarding the toxicity of intermediate degradation byproducts. Addressing these limitations will translate laboratory-scale findings into viable, large-scale environmental applications.
Future research should prioritize the development of advanced photocatalysts with high visible-light activity, ensuring enhanced degradation efficiency while maintaining long-term stability and low toxicity. Additionally, comprehensive toxicity assessments of degradation intermediates are essential to confirm the environmental safety of photocatalytic processes. Expanding the scope of research to include a broader range of plastic materials, optimizing reaction kinetics, and improving process scalability will be pivotal in bridging the gap between fundamental research and practical implementation.
This study underscores the importance of bibliometric analysis as a powerful tool for identifying research trends, collaboration networks, and knowledge gaps, ultimately guiding future innovation in photocatalytic microplastic degradation. Researchers can develop more effective, scalable, and sustainable solutions by leveraging these insights, accelerating progress toward global environmental remediation efforts and plastic pollution mitigation.
Furthermore, bibliometric analysis serves as a strategic tool for integrating scientific research with policy development. Bibliometric methods can inform evidence-based policymaking by quantitatively mapping the evolution of research themes, identifying influential studies, and revealing global collaboration networks. This approach is particularly relevant to addressing plastic pollution, where aligning scientific innovation with environmental regulation is essential. As such, bibliometric perspectives can support not only academic prioritization but also the formulation of informed and adaptive environmental policies.

Supplementary Materials

The following supporting information can be downloaded at: https://doi.org/10.17632/rpzv9k5s49.3 (accessed on 7 May 2025), PRISMA 2020 Checklist; R code for merging WoS and Scopus datasets; List of 204 articles used for the bibliometric analysis; Table S1: Annual scientific production and mean total citation per year; Table S2: Research contributions by top authors, institutions, and countries; Figure S1: Word cloud; Figure S2: Global authors collaboration density.

Author Contributions

Conceptualization, R.O.G. and Z.P.; methodology, R.O.G. and Z.P.; software, R.O.G. and Z.P.; validation, Z.P.; formal analysis, R.O.G.; resources, L.-A.d.K. and T.A.M.M.; data curation, R.O.G. and Z.P.; writing—original draft preparation, R.O.G.; writing—review and editing, Z.P., L.M.M., I.K., L.-A.d.K., and T.A.M.M.; visualization, R.O.G. and Z.P.; supervision, L.M.M., I.K., L.-A.d.K., and T.A.M.M.; project administration, L.M.M., I.K., L.-A.d.K., and T.A.M.M.; funding acquisition, L.M.M., I.K., L.-A.d.K., and T.A.M.M. All authors have read and agreed to the published version of the manuscript.

Funding

This research was funded by the Research for Marine Studies Catalytic Niche Area, College of Science, Engineering and Technology (CSET), University of South Africa (UNISA).

Data Availability Statement

The original contributions presented in this study are included in the article and Supplementary Materials. Further inquiries can be directed to the corresponding authors.

Acknowledgments

The authors gratefully acknowledge the Institute for Nanotechnology and Water Sustainability (iNanoWS) at the University of South Africa for providing the resources and facilities that supported this study.

Conflicts of Interest

The authors declare no conflict of interest.

Abbreviations

The following abbreviations are used in this manuscript:
AFMAtomic force microscopy
ATR-FTIRAttenuated total reflectance-Fourier transform infrared spectroscopy
CUUniversity of Calcutta
FTIRFourier-transform infrared spectroscopy
GOGraphene oxide
HDPEHigh-density polyethylene
LDPELow-density polyethylene
LEDLight emitting diode
MCPMulti-country publications
NFsNanofibers
NITNational Institute of Technology
NPNumber of publications
NPsNanoparticles
ONCOrganonanoclay
PAPolyamide
PANIPolyaniline
PEPolyethylene
PETPolyethylene terephthalate
PPPolypropylene
PSPolystyrene
PVCPolyvinyl chloride
PY startYear of publication start
ROSReactive oxygen species
SCMUSouth Central Minzu University
SCPSingle-country publication
SDGsSustainable Development Goals
SEMScanning electron microscopy
TCTotal citations
UANLUniversidad Autónoma de Nuevo León
UNIMOREUniversità di Modena e Reggio Emilia
UVUltraviolet
WHUWuhan University
WoSWeb of Science

References

  1. Parvez, M.S.; Ullah, H.; Faruk, O.; Simon, E.; Czédli, H. Role of microplastics in global warming and climate change: A review. Water Air Soil Pollut. 2024, 235, 201. [Google Scholar] [CrossRef]
  2. Dhaundiyal, A.; Mittal, A. Unveiling the microplastics: Sources, distribution, toxicological impacts, extraction methods, degradational strategies, paving the path to a sustainable future. Water Air Soil Pollut. 2024, 235, 691. [Google Scholar] [CrossRef]
  3. Ashrafy, A.; Liza, A.A.; Islam, M.N.; Billah, M.M.; Arafat, S.T.; Rahman, M.M.; Rahman, S.M. Microplastics pollution: A brief review of its source and abundance in different aquatic ecosystems. J. Hazard. Mater. Adv. 2023, 9, 100215. [Google Scholar] [CrossRef]
  4. Freeman, S.; Booth, A.M.; Sabbah, I.; Tiller, R.; Dierking, J.; Klun, K.; Rotter, A.; Ben-David, E.; Javidpour, J.; Angel, D.L. Between source and sea: The role of wastewater treatment in reducing marine microplastics. J. Environ. Manag. 2020, 266, 110642. [Google Scholar] [CrossRef] [PubMed]
  5. Amesho, K.T.T.; Chinglenthoiba, C.; Samsudin, M.S.A.B.; Lani, M.N.; Pandey, A.; Desa, M.N.M.; Suresh, V. Microplastics in the environment: An urgent need for coordinated waste management policies and strategies. J. Environ. Manag. 2023, 344, 118713. [Google Scholar] [CrossRef]
  6. Thacharodi, A.; Hassan, S.; Meenatchi, R.; Bhat, M.A.; Hussain, N.; Arockiaraj, J.; Ngo, H.H.; Sharma, A.; Nguyen, H.T.; Pugazhendhi, A. Mitigating Microplastic pollution: A critical review on the effects, remediation, and utilization strategies of microplastics. J. Environ. Manag. 2024, 351, 119988. [Google Scholar] [CrossRef] [PubMed]
  7. Ariza-Tarazona, M.C.; Siligardi, C.; Carreón-López, H.A.; Valdéz-Cerda, J.E.; Pozzi, P.; Kaushik, G.; Villarreal-Chiu, J.F.; Cedillo-González, E.I. Low environmental impact remediation of microplastics: Visible-light photocatalytic degradation of pet microplastics using bio-inspired C,N-TiO2/SiO2 photocatalysts. Mar. Pollut. Bull. 2023, 193, 115206. [Google Scholar] [CrossRef]
  8. Chokejaroenrat, C.; Watcharatharapong, T.; T-Thienprasert, J.; Angkaew, A.; Poompoung, T.; Chinwong, C.; Chirasatienpon, T.; Sakulthaew, C. Decomposition of microplastics using copper oxide/bismuth vanadate-based photocatalysts: Insight mechanisms and environmental impacts. Mar. Pollut. Bull. 2024, 201, 116205. [Google Scholar] [CrossRef]
  9. Qi, X.; Zhu, Y.; Song, L.; Peng, G.; Qu, W.; Xiong, J. Photocatalytic degradation of pet coupled to green hydrogen generation using flexible Ni2P/TiO2/C nanofiber film catalysts. Appl. Catal. A Gen. 2023, 656, 119130. [Google Scholar] [CrossRef]
  10. Sajad, S.; Allam, B.K.; Sillanpää, M.; Al-Farraj, S.; Singh, P.K.; Banerjee, S. Visible-light driven photodegradation of low-density polyethylene (ldpe) using BiOCL-ZrO2 nanocomposite: A sustainable strategy for mitigating plastic pollution. Nano-Struct. Nano-Objects 2024, 38, 101149. [Google Scholar] [CrossRef]
  11. Xie, A.; Jin, M.; Zhu, J.; Zhou, Q.; Fu, L.; Wu, W. Photocatalytic technologies for transformation and degradation of microplastics in the environment: Current achievements and future prospects. Catalysts 2023, 13, 846. [Google Scholar] [CrossRef]
  12. Lee, Q.Y.; Li, H. Photocatalytic degradation of plastic waste: A mini review. Micromachines 2021, 12, 907. [Google Scholar] [CrossRef]
  13. Sacco, N.A.; Zoppas, F.M.; Devard, A.; González Muñoz, M.d.P.; García, G.; Marchesini, F.A. Recent advances in microplastics removal from water with special attention given to photocatalytic degradation: Review of scientific research. Microplastics 2023, 2, 278–303. [Google Scholar] [CrossRef]
  14. Surana, M.; Pattanayak, D.S.; Yadav, V.; Singh, V.K.; Pal, D. An insight decipher on photocatalytic degradation of microplastics: Mechanism, limitations, and future outlook. Environ. Res. 2024, 247, 118268. [Google Scholar] [CrossRef] [PubMed]
  15. Hassaan, M.A.; El-Nemr, M.A.; Elkatory, M.R.; Ragab, S.; Niculescu, V.-C.; El Nemr, A. Principles of photocatalysts and their different applications: A review. Top. Curr. Chem. 2023, 381, 31. [Google Scholar] [CrossRef]
  16. Mohamadpour, F.; Amani, A.M. Photocatalytic systems: Reactions, mechanism, and applications. RSC Adv. 2024, 14, 20609–20645. [Google Scholar] [CrossRef]
  17. Djurišić, A.B.; He, Y.; Ng, A.M.C. Visible-light photocatalysts: Prospects and challenges. APL Mater. 2020, 8, 030903. [Google Scholar] [CrossRef]
  18. Phiri, Z.; Moja, N.T.; Nkambule, T.T.I.; de Kock, L.A. Utilization of biochar for remediation of heavy metals in aqueous environments: A review and bibliometric analysis. Heliyon 2024, 10, e25785. [Google Scholar] [CrossRef]
  19. Dube, V.; Phiri, Z.; Kuvarega, A.T.; Mamba, B.B.; de Kock, L.A. Exploring acid mine drainage treatment through adsorption: A bibliometric analysis. Environ. Sci. Pollut. Res. 2024, 31, 59659–59680. [Google Scholar] [CrossRef]
  20. Mohammed, A.M.; Aziz, F.; Mohtar, S.S.; Mhamad, S.A.; Ahmadu, B.; Nasir, M.U.; Muhammad, K.Y.; Aziz, M. A Review of research trends on the usage of photocatalysis for wastewater treatment: Bibliometric analysis. Sustain. Water Resour. Manag. 2023, 9, 88. [Google Scholar] [CrossRef]
  21. Aria, M.; Cuccurullo, C. Bibliometrix: An R-tool for comprehensive science mapping analysis. J. Informetr. 2017, 11, 959–975. [Google Scholar] [CrossRef]
  22. Wei, W.; Jiang, Z. A Bibliometrix-based visualization analysis of international studies on conversations of people with aphasia: Present and prospects. Heliyon 2023, 9, e16839. [Google Scholar] [CrossRef] [PubMed]
  23. van Eck, N.J.; Waltman, L. Software survey: VOSviewer, a computer program for bibliometric mapping. Scientometrics 2010, 84, 523–538. [Google Scholar] [CrossRef]
  24. van Eck, N.J.; Waltman, L. Visualizing bibliometric networks. In Measuring Scholarly Impact; Ding, Y., Rousseau, R., Wolfram, D., Eds.; Springer: Cham, Switzerland, 2014. [Google Scholar] [CrossRef]
  25. van Eck, N.J.; Waltman, L. Citation-based clustering of publications using CitNetExplorer and VOSviewer. Scientometrics 2017, 111, 1053–1070. [Google Scholar] [CrossRef]
  26. Celik, E.; Durmus, A.; Adizel, O.; Uyar, H.N. A bibliometric analysis: What do we know about metals(loids) accumulation in wild birds? Environ. Sci. Pollut. Res. 2021, 28, 10302–10334. [Google Scholar] [CrossRef] [PubMed]
  27. Pauna, V.H.; Buonocore, E.; Renzi, M.; Russo, G.F.; Franzese, P.P. The issue of microplastics in marine ecosystems: A bibliometric network analysis. Mar. Pollut. Bull. 2019, 149, 110612. [Google Scholar] [CrossRef]
  28. Kek, H.Y.; Tan, H.; Othman, M.H.D.; Lee, C.T.; Ahmad, F.B.J.; Ismail, N.D.; Nyakuma, B.B.; Lee, K.Q.; Wong, K.Y. Transforming pollution into solutions: A bibliometric analysis and sustainable strategies for reducing indoor microplastics while converting to value-added products. Environ. Res. 2024, 252, 118928. [Google Scholar] [CrossRef]
  29. Zhang, Y.; Pu, S.; Lv, X.; Gao, Y.; Ge, L. Global trends and prospects in microplastics research: A bibliometric analysis. J. Hazard. Mater. 2020, 400, 123110. [Google Scholar] [CrossRef]
  30. Mehta, N.; Kozielska, B. A systematic literature review and bibliometric analysis of sources and analytical approaches of indoor microplastics. Emerg. Contam. 2024, 10, 100274. [Google Scholar] [CrossRef]
  31. Hastuti, N.T.L.P.; Wahyuningsih, S.H.; Handayani, S.D. A bibliometric analysis of research developments of work stress on hospital nurses. J. Econ. Bus. 2022, 5, 249–262. [Google Scholar] [CrossRef]
  32. Echchakoui, S. Why and how to merge Scopus and Web of Science during bibliometric analysis: The case of sales force literature from 1912 to 2019. J. Mark. Anal. 2020, 8, 165–184. [Google Scholar] [CrossRef]
  33. Kasaraneni, H.J.; Rosaline, S. Automatic merging of Scopus and Web of Science data for simplified and effective bibliometric analysis. Ann. Data Sci. 2024, 11, 785–802. [Google Scholar] [CrossRef]
  34. Caputo, A.; Kargina, M. A user-friendly method to merge Scopus and Web of Science data during bibliometric analysis. J. Mark. Anal. 2022, 10, 82–88. [Google Scholar] [CrossRef]
  35. Kek, H.Y.; Saupi, S.B.M.; Tan, H.; Othman, M.H.D.; Nyakuma, B.B.; Goh, P.S.; Altowayti, W.A.H.; Qaid, A.; Wahab, N.H.A.; Lee, C.H.; et al. Ventilation strategies for mitigating airborne infection in healthcare facilities: A review and bibliometric analysis (1993–2022). Energy Build. 2023, 295, 113323. [Google Scholar] [CrossRef]
  36. Mongeon, P.; Paul-Hus, A. The journal coverage of Web of Science and Scopus: A comparative analysis. Scientometrics 2016, 106, 213–228. [Google Scholar] [CrossRef]
  37. Nyakuma, B.B.; Wong, S.; Mong, G.R.; Utume, L.N.; Oladokun, O.; Wong, K.Y.; Ivase, T.J.-P.; Abdullah, T.A.T. Bibliometric analysis of the research landscape on rice husks gasification (1995–2019). Environ. Sci. Pollut. Res. 2021, 28, 49467–49490. [Google Scholar] [CrossRef]
  38. Luing, W.S.; Ren, M.G.; Nyakuma, B.B.; Ngadi, N.; Yinn, W.K.; Hernández, M.M.; Armenise, S.; Tung, C.C. Upcycling of plastic waste to carbon nanomaterials: A bibliometric analysis (2000–2019). Clean Technol. Environ. Policy 2022, 24, 739–759. [Google Scholar] [CrossRef]
  39. Moher, D.; Liberati, A.; Tetzlaff, J.; Altman, D.G.; Prisma Group. Preferred reporting items for systematic reviews and meta-analyses: The PRISMA statement. Int. J. Surg. 2010, 8, 336–341. [Google Scholar] [CrossRef]
  40. Page, M.J.; McKenzie, J.E.; Bossuyt, P.M.; Boutron, I.; Hoffmann, T.C.; Mulrow, C.D.; Shamseer, L.; Tetzlaff, J.M.; Akl, E.A.; Brennan, S.E.; et al. The PRISMA 2020 statement: An updated guideline for reporting systematic reviews. BMJ 2021, 372, n71. [Google Scholar] [CrossRef]
  41. Rigueto, C.V.T.; Rosseto, M.; Alessandretti, I.; de Oliveira, R.; Wohlmuth, D.A.R.; Menezes, J.F.; Loss, R.A.; Dettmer, A.; Pizzutti, I.R. Gelatin films from wastes: A review of production, characterization, and application trends in food preservation and agriculture. Food Res. Int. 2022, 162, 112114. [Google Scholar] [CrossRef]
  42. Sharma, P.; Iqbal, H.M.N.; Chandra, R. Evaluation of pollution parameters and toxic elements in wastewater of pulp and paper industries in India: A case study. Case Stud. Chem. Environ. Eng. 2022, 5, 100163. [Google Scholar] [CrossRef]
  43. Pincheira, M.; Vecchio, M.; Giaffreda, R.; Kanhere, S.S. Cost-effective IoT devices as trustworthy data sources for a blockchain-based water management system in precision agriculture. Comput. Electron. Agric. 2021, 180, 105889. [Google Scholar] [CrossRef]
  44. Wang, H.; Li, X.; Zhao, X.; Li, C.; Song, X.; Zhang, P.; Huo, P.; Li, X. A review on heterogeneous photocatalysis for environmental remediation: From semiconductors to modification strategies. Chinese J. Catal. 2022, 43, 178–214. [Google Scholar] [CrossRef]
  45. Sadoff, C.W.; Borgomeo, E.; Uhlenbrook, S. Rethinking water for SDG 6. Nat. Sustain. 2020, 3, 346–347. [Google Scholar] [CrossRef]
  46. Bitaraf, M.; Amoozadeh, A. The first report of covalently grafted semiconductors; n-TiO2-P25@ECH@WO3 as a new, efficient, robust and visible-light-responsive photocatalyst. J. Chem. Technol. Biotechnol. 2021, 96, 963–970. [Google Scholar] [CrossRef]
  47. Yang, H.; Yang, B.; Chen, W.; Yang, J. Preparation and photocatalytic activities of TiO2-based composite catalysts. Catalysts 2022, 12, 1263. [Google Scholar] [CrossRef]
  48. Ariza-Tarazona, M.C.; Villarreal-Chiu, J.F.; Hernández-López, J.M.; De la Rosa, J.R.; Barbieri, V.; Siligardi, C.; Cedillo-González, E.I. Microplastic pollution reduction by a carbon and nitrogen-doped TiO2: Effect of pH and temperature in the photocatalytic degradation process. J. Hazard. Mater. 2020, 395, 122632. [Google Scholar] [CrossRef]
  49. Blanco-Gutiérrez, V.; Li, P.; Berzal-Cabetas, R.; Dos Santos-García, A.J. Exploring the photocatalytic activity of nanometric magnetite for PET materials degradation under UV light. J. Solid State Chem. 2022, 316, 123509. [Google Scholar] [CrossRef]
  50. Wang, X.; Zhu, Z.; Jiang, J.; Li, R.; Xiong, J. Preparation of heterojunction C3N4/WO3 photocatalyst for degradation of microplastics in water. Chemosphere 2023, 337, 139206. [Google Scholar] [CrossRef]
  51. Sarwan, B.; Acharya, A.D.; Kaur, S.; Pare, B. Visible light photocatalytic deterioration of polystyrene plastic using supported BiOCl nanoflower and nanodisk. Eur. Polym. J. 2020, 134, 109793. [Google Scholar] [CrossRef]
  52. Dinoop Lal, S.; Sunil Jose, T.; Rajesh, C.; Anju Rose Puthukkara, P.; Savitha Unnikrishnan, K.; Arun, K.J. Accelerated photodegradation of polystyrene by TiO2-polyaniline photocatalyst under UV radiation. Eur. Polym. J. 2021, 153, 110493. [Google Scholar] [CrossRef]
  53. Tan, S.Y.; Chong, W.C.; Sethupathi, S.; Pang, Y.L.; Sim, L.C.; Mahmoudi, E. Optimisation of aqueous phase low density polyethylene degradation by graphene oxide-zinc oxide photocatalysts. Chem. Eng. Res. Des. 2023, 190, 550–565. [Google Scholar] [CrossRef]
  54. Alanazi, M.Q.; Virk, P.; Alterary, S.S.; Awad, M.; Ahmad, Z.; Albadri, A.M.; Ortashi, K.M.; Ahmed, M.M.A.; Youseff, M.I.A.; Elobeid, E.A.; et al. Effect of potential microplastics in sewage effluent on Nile tilapia and photocatalytic remediation with zinc oxide nanoparticles. Environ. Pollut. 2023, 332, 121946. [Google Scholar] [CrossRef]
  55. Fakhri, L.A.; Ghanbarzadeh, B.; Dehghannya, J.; Hosseini, M.; Dadashi, S. Photo-catalytic and biotic degradation of polystyrene packaging film: Effect of zinc oxide photocatalyst nanoparticles and nanoclay. Chemosphere 2021, 283, 130972. [Google Scholar] [CrossRef]
  56. Ding, L.; Ouyang, Z.; Liu, P.; Wang, T.; Jia, H.; Guo, X. Photodegradation of microplastics mediated by different types of soil: The effect of soil components. Sci. Total Environ. 2022, 802, 149840. [Google Scholar] [CrossRef]
  57. Musthafa, J.M.; Mandal, B.K. CuO/Bi2O3/g-C3N4 nanoparticles for sunlight-mediated degradation of polyethylene terephthalate microplastic films. Opt. Mater. 2024, 154, 115701. [Google Scholar] [CrossRef]
  58. Zhang, Y.; Sun, T.; Zhang, D.; Shi, Z.; Zhang, X.; Li, C.; Wang, L.; Song, J.; Lin, Q. Enhanced photodegradability of PVC plastics film by codoping nano-graphite and TiO2. Polym. Degrad. Stab. 2020, 181, 109332. [Google Scholar] [CrossRef]
  59. Ojeba, I.; Helen, M.; Auta, S.; Salamah, U.; Sesan, I.; Aransiola, A. Micro- and nanoplastics in environment: Degradation, detection, and ecological impact. Int. J. Environ. Res. 2024, 18, 1. [Google Scholar] [CrossRef]
  60. Nakamura, H.; Suzuki, S.; Hironori, T. Citation lag analysis in supply chain research. Scientometrics 2011, 87, 221–232. [Google Scholar] [CrossRef]
  61. Tavakolizadeh-Ravari, M. A study on first citations of patents through a combination of Bradford’s distribution, cox regression and life tables method. J. Inf. Sci. 2020, 46, 496–507. [Google Scholar] [CrossRef]
  62. Gamelas, S.R.D.; Tomé, J.P.C.; Tomé, A.C.; Lourenço, L.M.O. Advances in photocatalytic degradation of organic pollutants in wastewaters: Harnessing the power of phthalocyanines and phthalocyanine-containing materials. RSC Adv. 2023, 13, 33957–33993. [Google Scholar] [CrossRef]
  63. Fan, W.; Aghabalayev, F.; Ahmad, M. The role of global collaboration in environmental technology development, natural resources, and marine energy generation technologies toward carbon neutrality in knowledge-based economies. Environ. Sci. Pollut. Res. 2023, 30, 75863–75878. [Google Scholar] [CrossRef]
  64. Tofa, T.S.; Kunjali, K.L.; Paul, S.; Dutta, J. Visible light photocatalytic degradation of microplastic residues with zinc oxide nanorods. Environ. Chem. Lett. 2019, 17, 1341–1346. [Google Scholar] [CrossRef]
  65. Uheida, A.; Mejía, H.G.; Abdel-Rehim, M.; Hamd, W.; Dutta, J. Visible light photocatalytic degradation of polypropylene microplastics in a continuous water flow system. J. Hazard. Mater. 2021, 406, 124299. [Google Scholar] [CrossRef]
  66. Ariza-Tarazona, M.C.; Villarreal-Chiu, J.F.; Barbieri, V.; Siligardi, C.; Cedillo-González, E.I. New strategy for microplastic degradation: Green photocatalysis using a protein-based porous N-TiO2 semiconductor. Ceram. Int. 2019, 45, 9618–9624. [Google Scholar] [CrossRef]
  67. Zhao, H.; Li, R.K.Y. A study on the photo-degradation of zinc oxide (ZnO) filled polypropylene nanocomposites. Polymer 2006, 47, 3207–3217. [Google Scholar] [CrossRef]
  68. Nabi, I.; Bacha, A.-U.-R.; Li, K.; Cheng, H.; Wang, T.; Liu, Y.; Ajmal, S.; Yang, Y.; Feng, Y.; Zhang, L. Complete photocatalytic mineralization of microplastic on TiO2 nanoparticle film. iScience 2020, 23, 101326. [Google Scholar] [CrossRef]
  69. Cao, B.; Wan, S.; Wang, Y.; Guo, H.; Ou, M.; Zhong, Q. Highly-efficient visible-light-driven photocatalytic H2 evolution integrated with microplastic degradation over MXene/ZnₓCd1₋ₓS photocatalyst. J. Colloid Interface Sci. 2022, 605, 311–319. [Google Scholar] [CrossRef]
  70. Zhao, X.; Li, Z.; Chen, Y.; Shi, L.; Zhu, Y. Solid-phase photocatalytic degradation of polyethylene plastic under UV and solar light irradiation. J. Mol. Catal. A Chem. 2007, 268, 101–106. [Google Scholar] [CrossRef]
  71. Jiang, R.; Lu, G.; Yan, Z.; Liu, J.; Wu, D.; Wang, Y. Microplastic degradation by hydroxy-rich bismuth oxychloride. J. Hazard. Mater. 2021, 405, 124247. [Google Scholar] [CrossRef]
  72. Zinc, P.; Nanorod, O.; Tofa, T.S.; Ye, F.; Kunjali, K.L. Enhanced visible light photodegradation of microplastic fragments with plasmonic catalyst. Catalyst 2019, 9, 819. [Google Scholar] [CrossRef]
  73. Zan, L.; Fa, W.; Wang, S. Novel photodegradable low-density polyethylene- TiO2 nanocomposite film. Environ. Sci. Technol. 2006, 40, 1681–1685. [Google Scholar] [CrossRef]
  74. Llorente-García, B.E.; Hernández-López, J.M.; Zaldívar-Cadena, A.A.; Siligardi, C.; Cedillo-González, E.I. First insights into photocatalytic degradation of HDPE and LDPE microplastics by a mesoporous N-TiO2 coating: Effect of size and shape of microplastics. Coatings 2020, 10, 658. [Google Scholar] [CrossRef]
  75. Liang, W.; Luo, Y.; Song, S.; Dong, X.; Yu, X. High photocatalytic degradation activity of polyethylene containing polyacrylamide grafted TiO2. Polym. Degrad. Stab. 2013, 98, 1754–1761. [Google Scholar] [CrossRef]
  76. Domínguez-Jaimes, L.P.; Cedillo-González, E.I.; Luévano-Hipólito, E.; Acuña-Bedoya, J.D.; Hernández-López, J.M. Degradation of primary nanoplastics by photocatalysis using different anodized TiO2 structures. J. Hazard. Mater. 2021, 413, 125452. [Google Scholar] [CrossRef]
  77. Zhao, X.; Li, Z.; Chen, Y.; Shi, L.; Zhu, Y. Enhancement of photocatalytic degradation of polyethylene plastic with CuPc modified TiO2 photocatalyst under solar light irradiation. Appl. Surf. Sci. 2008, 254, 1825–1829. [Google Scholar] [CrossRef]
  78. Chakrabarti, S.; Chaudhuri, B.; Bhattacharjee, S.; Das, P.; Dutta, B.K. Degradation mechanism and kinetic model for photocatalytic oxidation of PVC-ZnO composite film in presence of a sensitizing dye and UV radiation. J. Hazard. Mater. 2008, 154, 230–236. [Google Scholar] [CrossRef]
  79. Zhou, D.; Luo, H.; Zhang, F.; Wu, J.; Yang, J.; Wang, H. Efficient photocatalytic degradation of the persistent PET fiber-based microplastics over Pt nanoparticles decorated N-doped TiO2 nanoflowers. Adv. Fiber Mater. 2022, 4, 1094–1107. [Google Scholar] [CrossRef]
  80. Fernando, S.S.; Christensen, P.A.; Egerton, T.A.; White, J.R. Carbon dioxide evolution and carbonyl group development during photodegradation of polyethylene and polypropylene. Polym. Degrad. Stab. 2007, 92, 2163–2172. [Google Scholar] [CrossRef]
  81. Zan, L.; Wang, S.; Fa, W.; Hu, Y.; Tian, L.; Deng, K. Solid-phase photocatalytic degradation of polystyrene with modified nano-TiO2 catalyst. Polymer 2006, 47, 8155–8162. [Google Scholar] [CrossRef]
  82. Thomas, R.T.; Nair, V.; Sandhyarani, N. TiO2 nanoparticle assisted solid phase photocatalytic degradation of polythene film: A mechanistic investigation. Colloids Surfaces A Physicochem. Eng. Asp. 2013, 422, 1–9. [Google Scholar] [CrossRef]
  83. Chakravorty, A.; Roy, S. A review of photocatalysis, basic principles, processes, and materials. Sustain. Chem. Environ. 2024, 8, 100155. [Google Scholar] [CrossRef]
Figure 1. Flow diagram illustrating the PRISMA search criteria for identifying relevant scholarly articles on nano/microplastic photocatalytic degradation. The asterisk (*) in the search terms is a wildcard symbol used to capture all word variants beginning with the root.
Figure 1. Flow diagram illustrating the PRISMA search criteria for identifying relevant scholarly articles on nano/microplastic photocatalytic degradation. The asterisk (*) in the search terms is a wildcard symbol used to capture all word variants beginning with the root.
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Figure 2. SEM micrographs of PET MPs (a) before and (b) after photocatalytic degradation for 120 h [7]; (ce) FTIR spectra of LDPE, PP, and PA before and after being exposed to a photo-Fenton catalytic process using 0.5CuO/BiVO4@300 °C for 14 days [8]; (f) AFM and (g) SEM images of PS under BiOCl nanodisk after 90 h visible light irradiation [51]; (h) SEM images and (i) FTIR spectra of PS before and after photodegradation [55]; (j) SEM images of pristine MPs and photodegraded MPs after 20 days of treatment with and without the presence of soil [56]; (k) SEM measurement of Nano-G/TiO2/PVC composite film after exposure to light for 30 h [58].
Figure 2. SEM micrographs of PET MPs (a) before and (b) after photocatalytic degradation for 120 h [7]; (ce) FTIR spectra of LDPE, PP, and PA before and after being exposed to a photo-Fenton catalytic process using 0.5CuO/BiVO4@300 °C for 14 days [8]; (f) AFM and (g) SEM images of PS under BiOCl nanodisk after 90 h visible light irradiation [51]; (h) SEM images and (i) FTIR spectra of PS before and after photodegradation [55]; (j) SEM images of pristine MPs and photodegraded MPs after 20 days of treatment with and without the presence of soil [56]; (k) SEM measurement of Nano-G/TiO2/PVC composite film after exposure to light for 30 h [58].
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Figure 3. (a) Distribution of document types in microplastics research; (b) Annual scientific production and citations per year for publications on microplastics.
Figure 3. (a) Distribution of document types in microplastics research; (b) Annual scientific production and citations per year for publications on microplastics.
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Figure 4. (a) Leading journal sources and (b) production trends in photocatalytic degradation of nano/microplastics research.
Figure 4. (a) Leading journal sources and (b) production trends in photocatalytic degradation of nano/microplastics research.
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Figure 5. Three field plot showing the relation among authors’ keywords, authors, and sources.
Figure 5. Three field plot showing the relation among authors’ keywords, authors, and sources.
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Figure 6. Visualization of research contributions by (a) author, (b) institution, and (c) country, including (d) collaboration distribution for single- vs. multi-country publications by country.
Figure 6. Visualization of research contributions by (a) author, (b) institution, and (c) country, including (d) collaboration distribution for single- vs. multi-country publications by country.
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Figure 7. Affiliation production over time.
Figure 7. Affiliation production over time.
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Figure 8. Density visualization map of keyword co-occurrence related to the photocatalytic degradation of nano/microplastics in aquatic environments. Note: Warmer colors (e.g., red, yellow) represent areas of higher term co-occurrence, while cooler colors (e.g., blue, green) represent lower-density regions (VOSviewer 1.6.20).
Figure 8. Density visualization map of keyword co-occurrence related to the photocatalytic degradation of nano/microplastics in aquatic environments. Note: Warmer colors (e.g., red, yellow) represent areas of higher term co-occurrence, while cooler colors (e.g., blue, green) represent lower-density regions (VOSviewer 1.6.20).
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Figure 9. (a) Network visualization and (b) overlay map showing keyword co-occurrence related to the photocatalytic degradation of nano/microplastics in aquatic environments, generated using VOSviewer version 1.6.20.
Figure 9. (a) Network visualization and (b) overlay map showing keyword co-occurrence related to the photocatalytic degradation of nano/microplastics in aquatic environments, generated using VOSviewer version 1.6.20.
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Figure 10. Global collaboration network of countries involved in photocatalytic degradation research of nano- and microplastics. The map illustrates links to international co-authorships based on bibliometric data. Countries are color-coded by publication volume, with darker shades indicating higher research output—China is the most prolific contributor. The connecting lines represent collaborative ties, with line thickness corresponding to the strength or frequency of co-authored publications between countries.
Figure 10. Global collaboration network of countries involved in photocatalytic degradation research of nano- and microplastics. The map illustrates links to international co-authorships based on bibliometric data. Countries are color-coded by publication volume, with darker shades indicating higher research output—China is the most prolific contributor. The connecting lines represent collaborative ties, with line thickness corresponding to the strength or frequency of co-authored publications between countries.
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Figure 11. Global authors collaboration network.
Figure 11. Global authors collaboration network.
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Figure 12. Trend topics related to the photocatalytic degradation of nano- and microplastics. Each horizontal line represents the active period during which a given topic appeared in the literature. The position of each dot indicates the year of peak activity for that topic, while the size of the dot corresponds to the frequency of keyword occurrence or publication volume in that year. Larger dots signify higher research interest. Emerging topics such as "photocatalysis," "microplastics," and "polyethylene terephthalate" show strong recent growth in scholarly attention.
Figure 12. Trend topics related to the photocatalytic degradation of nano- and microplastics. Each horizontal line represents the active period during which a given topic appeared in the literature. The position of each dot indicates the year of peak activity for that topic, while the size of the dot corresponds to the frequency of keyword occurrence or publication volume in that year. Larger dots signify higher research interest. Emerging topics such as "photocatalysis," "microplastics," and "polyethylene terephthalate" show strong recent growth in scholarly attention.
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Table 1. An overview of key primary information from the bibliometric analysis.
Table 1. An overview of key primary information from the bibliometric analysis.
Bibliometric MeasurementResult
Duration/period2005–2024
Sources112
Articles204
Annual growth rate (%)17.94
Document average age (years)5.91
Average citations per document31.75
Keywords Plus (ID)624
Author’s Keywords (DE)522
Authors794
Authors of single-authored documents2
Single-authored documents2
Co-authors per document5.42
International co-authorships (%)25.98
Table 2. Summary of photocatalysts used in nano/microplastic degradation applications.
Table 2. Summary of photocatalysts used in nano/microplastic degradation applications.
PhotocatalystSynthesis MethodNano- and Microplastic TypeIrradiation SourceReaction Time (h)Degradation Efficiency (%)Ref.
C,N-TiO2/SiO2 (TS-ME)Extrapallial fluid from Mytilus edulisPET50 W LED visible light1209.35–16.22 at pH 6 and 8[7]
C,N-TiO2/SiO2 (TS-MG)Extrapallial fluid from Mytilus galloprovincialis9.35–16.22 at pH 6 and 8[7]
CuO/BiVO4Modified nanoscale CuO/BiVO4LDPE, PP, and PASimulated solar light8 h per day for 14 days[8]
Ni2P/TiO2/C NFsElectrospinning, heat treatment, hydrothermal treatment, phosphate treatmentPET500 W mercury lamp[9]
BiOCl–ZrO2Co-precipitationLDPEVisible light irradiation2448.67[10]
C,N-TiO2Green bio-inspired synthesis using mussel extrapallial fluidHDPE50 W LED lamp (400–800 nm)5071.77 ± 1.88[48]
Fe3O4Solvothermal methodPETUV-A radiation192 (8 days)[49]
WO3/g-C3N4Hydrothermal methodPETVisible light (300 W xenon lamp10 (for WO3 synthesis)High H2 evolution indicated effective degradation[50]
BiOCl (Nanoflower)Solution-cast technique;PS500 W Halogen luminaire90[51]
BiOCl (Nanodisk)Reaction of Bi(NO3)3 and FeCl3
TiO2-Polyaniline (PANI)Chemical oxidative polymerizationPSUV lamp (30 W, wavelength 253 nm)1000[52]
Graphene Oxide-Zinc Oxide (GO-ZnO)Precipitation method for ZnO; Ultrasonication for GO-ZnOLDPEUV Light (40 W)239.47[53]
Zinc Oxide Nanoparticles (ZnONPs)Nano precipitation techniquePVC, PE, PS, PP, PETUV light (365 nm)175[54]
Zinc Oxide (ZnO-NPs)PSUV lamp (30 W, λ = 254 nm)300 [55]
Organonanoclay (ONC)
PS-ONC-ZnO (Nanocomposite)
Soil Components (Clay, Iron Oxides, MnO2)Not specified in detailPET500 W Xenon lamp (wavelength range 295–2500 nm)480 (20 days)28.9%[56]
CuO/Bi2O3/g-C3N4Sol-gel methodPETSunlight240 (10 days)41.60%[57]
TiO2 and Nano-graphiteCodoping in PVC matrixPVC composite film300 W medium-pressure UV lamp (365 nm)3017.24 (for Nano-G/TiO2/PVC)[58]
Table 3. Metrics of top journals in photocatalytic degradation of nano/microplastics research.
Table 3. Metrics of top journals in photocatalytic degradation of nano/microplastics research.
Sourceh_indexg_indexm_indexTCNPPY_start
Polymer Degradation and Stability15230.789667232006
Journal of Hazardous Materials9120.5291072122008
Journal of Applied Polymer Science790.46716292010
Journal of Environmental Chemical Engineering7101.167180102019
Chemical Engineering Journal4424342023
Applied Surface Science330.17616132008
Chemosphere330.2147432011
Polymer Bulletin330.53432019
Polymer Composites340.1885642009
ACS Catalysis220.58322021
Composites Part B-Engineering220.255522017
Environmental Chemistry Letters220.33335022019
Environmental Pollution221832023
Environmental Science & Technology220.10513922006
Environmental Science-Nano220.53722021
Table 4. Citation metrics and publication statistics for the top ten researchers.
Table 4. Citation metrics and publication statistics for the top ten researchers.
Authorh_indexg_indexm_indexTCNPPY_start
Cedillo-González E891.33378492019
Wang H8110.5250112009
Zan L770.36844272006
Deng K660.31628362006
Fa W670.31637572006
Liu J681.525482021
Nakatani H670.3759572009
Siligardi C66163162019
Ariza-Tarazona M550.83352752019
Hernández-López J55154452020
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Gembo, R.O.; Phiri, Z.; Madikizela, L.M.; Kamika, I.; de Kock, L.-A.; Msagati, T.A.M. Global Research Trends in Photocatalytic Degradation of Microplastics: A Bibliometric Perspective. Microplastics 2025, 4, 35. https://doi.org/10.3390/microplastics4030035

AMA Style

Gembo RO, Phiri Z, Madikizela LM, Kamika I, de Kock L-A, Msagati TAM. Global Research Trends in Photocatalytic Degradation of Microplastics: A Bibliometric Perspective. Microplastics. 2025; 4(3):35. https://doi.org/10.3390/microplastics4030035

Chicago/Turabian Style

Gembo, Robert O., Zebron Phiri, Lawrence M. Madikizela, Ilunga Kamika, Lueta-Ann de Kock, and Titus A. M. Msagati. 2025. "Global Research Trends in Photocatalytic Degradation of Microplastics: A Bibliometric Perspective" Microplastics 4, no. 3: 35. https://doi.org/10.3390/microplastics4030035

APA Style

Gembo, R. O., Phiri, Z., Madikizela, L. M., Kamika, I., de Kock, L.-A., & Msagati, T. A. M. (2025). Global Research Trends in Photocatalytic Degradation of Microplastics: A Bibliometric Perspective. Microplastics, 4(3), 35. https://doi.org/10.3390/microplastics4030035

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