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. 2026 Jul 2;16(34):31109–31139. doi: 10.1039/d6ra02330d

Organic polymers tuned the photocatalytic activity of inorganic semiconductors in polymer-semiconductor composites: a critical review

Muhammad Arif a,✉
PMCID: PMC13325529  PMID: 42395781

Abstract

Organic polymer-semiconductor composites have emerged as photocatalytic materials due to their tunable electronic structures, strong visible-light absorption, and flexible interfacial design. In contrast to pure inorganic photocatalysts (semiconductors), these hybrid systems enable the precise modulation of charge separation, light harvesting, and surface reactivity through rational polymer engineering and composite architecture. This review critically examines the main factors governing the photocatalytic activity of organic polymer-semiconductor composites arising from the presence of organic polymers based on structure–property–performance relationships. The fundamental photocatalytic mechanisms, polymer classifications, interfacial charge transfer pathways, and design of organic polymer-semiconductors are systematically discussed. Special attention is given to activity tuning through band gap engineering, morphology control, and recombination suppression. Recent advances in environmental remediation and energy conversion applications are analyzed, alongside current challenges and future research directions. This review provides a unified framework for understanding and optimizing organic polymer-semiconductor photocatalysts, providing guidance for next-generation sustainable photocatalytic systems.


Organic polymer-semiconductor composites have emerged as photocatalytic materials due to their tunable electronic structures, strong visible-light absorption, and flexible interfacial design.graphic file with name d6ra02330d-ga.jpg

1. Introduction

The rapid industrialization and population growth of modern society have resulted in severe environmental pollution and an increase in energy demand, posing significant threats to ecosystems and human health.1–3 Persistent organic pollutants,4 toxic dyes,5 pharmaceutical residues,6 and greenhouse gases (like carbon dioxide7) are particularly challenging owing to their chemical stability and resistance to conventional treatment methods. In this context, photocatalysis has emerged as an optimistic green technology capable of utilizing abundant solar energy to drive chemical reactions for environmental remediation8 and sustainable energy production.9

Photocatalytic processes enable the degradation of organic pollutants,10 hydrogen generation from water splitting,11 and CO2 reduction12,13 under mild reaction conditions without the need for excessive chemical inputs. Traditional inorganic semiconductor photocatalysts are metal oxides,14 metal sulfides,15 and g-C3N4,16 which have been extensively investigated owing to their suitable band structures and chemical stability. However, their practical application remains hampered by intrinsic drawbacks like limited visible-light absorption, rapid electron–hole recombination, poor selectivity, and poor interfacial charge transfer efficiency. These limitations significantly reduce quantum efficiency and hinder large-scale implementation.

Hybrid photocatalytic systems based on organic polymer-semiconductor composites have attracted significant attention in recent years to resolve these challenges.17–21 Organic polymers have unique advantages that distinguish them from purely inorganic materials. Their molecular structures can be precisely tailored through chemical synthesis, which enables fine control over optical absorption,22–24 electronic properties,25 selectivity towards pollutants,20,26 stimuli-responsive behaviors,21 and interfacial interactions.17 In particular, π-conjugated polymers,27,28 stimuli-responsive polymers,21 and conducting polymers29 exhibit strong visible-light absorption, reversible environmental effects, and efficient charge-transport characteristics, which make them ideal candidates for coupling with inorganic semiconductors.

When organic polymers are integrated with semiconductors, they can play multiple functional roles such as acting as photo- and environmental-sensitizers, charge mediators, surface modifiers, or protective layers.30–33 This multifunctionality allows organic polymer-semiconductor composites to overcome the fundamental limitations of conventional photocatalysts by extending light absorption to the visible region, facilitating directional charge transfer, imparting stimuli-responsive behavior, and suppressing charge carrier recombination. Furthermore, polymer-based modifications provide an effective strategy to tune the surface chemistry and improve reactant adsorption, which are critical for enhancing photocatalytic reaction kinetics.34,35

Most available reviews primarily focus on the general enhancement of photocatalytic activity through composite formation, but they rarely provide a systematic and mechanistic analysis of how organic polymers specifically tune the electronic, structural, and interfacial properties of semiconductor photocatalysts. In particular, the roles of polymers in band structure modulation, charge carrier separation, interfacial charge transfer pathways, surface functionalization, and stability enhancement are discussed superficially or only qualitatively. Furthermore, many reviews emphasize inorganic heterojunction systems, while the unique contributions of functional organic polymers such as conductive polymers, biopolymers, and porous polymer networks remain insufficiently compared or critically evaluated.36–40 Another major limitation is the lack of correlation between the physicochemical properties of polymers (e.g., functional groups, conductivity, porosity, and molecular architecture) and their photocatalytic performance, which hinders the development of rational design strategies. Furthermore, current literature reviews seldom address the scalability, long-term stability, environmental compatibility, and real wastewater applications of polymer-semiconductor composites. Therefore, a comprehensive and critical review that systematically evaluates the mechanistic roles of organic polymers in tuning semiconductor photocatalysis and establishes structure–property–performance relationships is still needed to guide future material design and practical applications.

The aim of this review is to establish a coherent framework for understanding how organic polymers can be strategically employed to tune the photocatalytic activity of organic polymer-semiconductor composites. The insights presented herein are expected to guide the rational design of next-generation polymer-semiconductor photocatalysts for efficient, stable, and sustainable environmental and energy-related applications.

2. Fundamentals of photocatalysis

Photocatalysis is a light-driven process in which a photocatalyst absorbs photons and converts their energy into chemical reactions through the generation of reactive charge carriers.

2.1. Light absorption and charge carrier generation

The fundamental step in photocatalysis is the absorption of photons with energy equal to or greater than the band gap of the photocatalyst. Upon illumination, electrons in the valence band (VB) of a semiconductor are excited to the conduction band (CB), leaving holes in the VB. These photogenerated electrons and holes act as reductive and oxidative species, respectively, as shown in Fig. 1. In traditional pure semiconductors, this process is largely restricted to ultraviolet light due to the wide band gaps that limit solar utilization.

Fig. 1. Photocatalytic degradation mechanism of pollutants using pure semiconductors.

Fig. 1

Organic polymers (particularly conjugated and conducting polymers) significantly enhance light absorption by extending the absorption edge into the visible region through π–π* transitions. When combined with semiconductors, polymers act as photosensitizers or co-absorbers and generate additional charge carriers under visible light. Polymer-semiconductor composites exhibit higher photon utilization efficiency than bare semiconductors, leading to increased charge carrier generation and improved photocatalytic performance under solar irradiation.41,42

2.2. Charge separation and migration

Once charge carriers are generated, their effective separation and migration to the catalyst surface are critical for initiating the redox reactions. In single-component semiconductors, electrons and holes tend to recombine rapidly due to short diffusion lengths and a lack of internal driving forces. This recombination severely limits the photocatalytic efficiency although the materials have strong light absorption.

The introduction of organic polymers creates heterojunction interfaces that promote directional charge migration. Polymers can selectively extract electrons or holes depending on their HOMO–LUMO alignment relative to the semiconductor bands. Compared with pristine semiconductors, polymer-semiconductor composites exhibit prolonged charge carrier lifetimes and enhanced migration efficiency, which directly translates into higher photocatalytic activity, as shown in Fig. 2.27 Nevertheless, the effectiveness of this process depends strongly on the nature of the interfacial charge transfer mechanism, as discussed in detail below.

Fig. 2. Stabilization of electrons and holes in semiconductors by the cationic or anionic components of organic polymers.

Fig. 2

2.3. Interfacial charge transfer mechanisms

Interfacial charge transfer mechanisms define how photogenerated electrons and holes are redistributed across polymer-semiconductor interfaces. These mechanisms determine the balance between the charge separation efficiency and redox capability and hence control the overall photocatalytic performance.

The historical evolution of photocatalytic heterojunction systems from simple charge-separation models to more advanced mechanisms capable of simultaneously achieving efficient charge separation and strong redox capability is illustrated in Fig. 3(A–F). The figure demonstrates how the understanding of interfacial charge transfer has progressed over time to overcome the fundamental limitations (rapid electron–hole recombination and loss of redox power) of conventional semiconductor photocatalysts, as shown in Fig. 3(A). Initially, photocatalytic research focused on type-II heterojunctions, in which photogenerated electrons and holes migrate to different semiconductors and results in the effective spatial separation of charge carriers, as shown in Fig. 3(D). Although this mechanism significantly suppresses charge recombination, it also reduces the oxidation and reduction potentials of the remaining charge carriers because electrons accumulate in a less negative CB, while holes accumulate in a less positive VB.43 Consequently, type-II heterojunctions exhibit limited performance in demanding photocatalytic reactions like water splitting and CO2 reduction.

Fig. 3. Photocatalytic reaction mechanisms of semiconductor-polymer composites: (A) only polymer semiconductor, (B) liquid phase Z-scheme, (C) all-solid-state Z-scheme, (D) type-II, (E) direct Z-scheme, and (F) S-scheme.

Fig. 3

On the other hand, researchers have also developed a traditional Z-scheme photocatalytic system to overcome the issue of electron–hole recombination, inspired by natural photosynthesis.44 In this configuration, two photocatalysts are connected through an Fe3+/Fe2+ electron mediator that allows low-energy electrons and holes to recombine while preserving highly energetic charge carriers for redox reactions, as shown in Fig. 3(B). This approach successfully retains strong oxidation and reduction abilities. However, the use of Fe2+ and Fe3+ ions as electron mediators introduces several practical disadvantages, like backward reactions, instability, and complex system design. As a result, the traditional Z-scheme mechanism has limited applicability in practical photocatalytic systems. To address these shortcomings, an all-solid-state Z-scheme heterojunction was proposed, as shown in Fig. 3(C), in which solid conductors like noble metals are used as electron mediators. This design improves the charge transfer efficiency and system stability compared with traditional Z-schemes. However, subsequent studies have revealed that the actual charge transfer behavior in many solid-state Z-scheme systems differs from the originally proposed mechanism due to Fermi-level equilibration and the formation of Schottky barriers, which can hinder charge migration and increase fabrication complexity.

Researchers have proposed a direct Z-scheme heterojunction to resolve these challenges, as shown in Fig. 3(E), in which two semiconductors are brought into direct contact without any external electron mediator.45 This design simplifies the system and improves the interfacial charge transfer while maintaining strong redox capability. Still, questions remain regarding the actual charge migration pathway and the scientific interpretation of the mechanism. To resolve these issues, the S-scheme (step-scheme) heterojunction concept was introduced, as shown in Fig. 3(F). The S-scheme model provides a more rigorous description of charge transfer by considering the Fermi-level differences, built-in electric fields, and band bending at the interface. In this mechanism, low-energy electrons and holes recombine selectively at the interface, while highly energetic electrons and holes are retained for reduction and oxidation reactions, respectively.46,47 This unique charge-selection process simultaneously maximizes the charge separation efficiency and redox capability, resulting in superior photocatalytic performance. Therefore, the development of the S-scheme heterojunction represents a major milestone in photocatalysis because it provides a scientifically accurate framework for explaining charge transfer phenomena and designing highly efficient photocatalytic systems.48

Bhankhar et al.49 reported the synthesis and photocatalytic activity of Li-doped NiO-polyaniline (LDN-PAn) composites with different content of LDN during composite formation. The LUMO of PAn has higher energy than the CB of LDN, while the HOMO of PAn has lower energy than the VB of LDN. The electrons present in the LUMO of PAn shift to the CB of LDN and convert O2 molecules into ˙O2− radicals. These radicals degrade the MB dye. The type-II mechanism was reported by Sajith et al.50 They photocatalytically degraded malachite green (MG) using polyaniline-titanium oxide (PAn-TiO2) composites. In this mechanism, the electron of PAn (present in the LUMO) shifts into the conduction band of TiO2 and holes from the VB of TiO2 to the HOMO of PAn. This shift of electrons from the LUMO of PAn to the CB of TiO2 increases the rate of conversion of O2 into ˙O2− and hence increases the degradation rate of the dye. The Z-scheme mechanism overcomes these limitations by allowing low-energy electrons and holes to recombine while retaining highly energetic charge carriers.51 In polymer-semiconductor composites, polymers act as solid-state electron mediators that enable efficient Z-scheme charge transfer without sacrificial agents. Compared with type-II systems, Z-scheme architectures exhibit superior redox ability and higher quantum efficiency, particularly in solar fuel production and advanced oxidation processes.11

The evolution illustrated in Fig. 3(A–F) is particularly significant for organic polymer-semiconductor composites. Organic polymers and semiconductors possess tunable electronic structures, adjustable energy levels, extended visible-light absorption, and excellent interfacial engineering capability. These properties make them ideal candidates for constructing advanced direct Z-scheme and S-scheme heterojunctions. Polymer-based S-scheme heterojunctions can achieve stronger redox power, broader solar-light utilization, more efficient charge separation, and enhanced photocatalytic stability compared with conventional type-II systems. Therefore, Fig. 3 not only describes the historical development of heterojunction photocatalysts but also highlights the scientific progression toward increasingly efficient charge-transfer architectures, which culminate in the S-scheme concept. This is currently regarded as one of the most suitable strategies for designing next-generation organic polymer-semiconductor photocatalysts.

2.4. Surface redox reactions

After successful charge separation and migration, photogenerated electrons and holes participate in surface redox reactions. Electrons typically reduce adsorbed species like oxygen, protons, pollutants, or CO2, while holes oxidize water or organic pollutants. The efficiency of these reactions depends on the availability of active sites, the surface adsorption strength, and the redox potential of the charge carriers.

Organic polymers contribute to surface reaction enhancement by introducing functional groups that improve reactant adsorption and facilitate electron transfer. Polymer-semiconductor composites show enhanced surface reaction kinetics due to improved charge accessibility and chemical affinity compared to pure semiconductors, as shown in Fig. 2. However, excessive polymer coverage can block active sites, which highlights the need for an optimized interfacial design.

The photocatalytic efficiency of organic polymer-semiconductor composites is governed by a sequence of interconnected processes, such as light absorption, charge generation, separation, migration, and surface reactions. Among interfacial charge transfer mechanisms, type-I systems provide limited improvement due to recombination, type-II systems improve charge separation but sacrifice redox strength, and Z-scheme and S-scheme systems provide an optimal balance between carrier separation and redox capability. In polymer-semiconductor composites, S-scheme architectures generally demonstrate the highest photocatalytic performance, followed closely by Z-scheme systems.

Understanding these fundamental mechanisms is essential for rationally designing organic polymer-semiconductor composites with tailored activity. These principles form the scientific foundation for the activity-tuning strategies discussed in Section 4, where polymer chemistry, energy-level alignment, and structural engineering are systematically optimized.

3. Organic polymer-semiconductor composites

3.1. Classification of organic polymers used in photocatalytic composites

Organic polymers are further divided into (i) biological organic polymers and (ii) synthesized organic polymers, which are used to form composites. Each class of these organic polymers have significant effect on the photocatalytic performance of semiconductors as given in Table 1.

Table 1. Comparative performance of polymer-semiconductor photocatalytic composites.

Type of polymer-semiconductor composite Representative polymers Effect on light absorption Charge separation and transfer efficiency Advantages in activity tuning Photocatalytic performance trend Challenges
Conjugated polymer-semiconductor composites Polythiophene, g-C3N4, polyfluorene Strong visible-light absorption through π–π* transitions Moderate to high, depends on interfacial contact Extends light absorption, improves charge delocalization, facilitates Z- or S-scheme formation High degradation rates under visible light, moderate energy conversion Photodegradation under prolonged irradiation, limited conductivity
Conducting polymer-semiconductor composites Polypyrrole, polyaniline, poly(3,4-ethylenedioxythiophene) (PEDOT) Moderate visible absorption High due to improved electrical conductivity Improved electron mobility, suppressed recombination, efficient charge separation Very high reaction kinetics in pollutant degradation Loss of conductivity, over-oxidation, structural instability
Polymeric semiconductor–semiconductor composites Covalent organic frameworks (COFs), conjugated microporous polymers (CMPs), g-C3N4/TiO2 Tunable visible absorption High when well-aligned (Z-/S-scheme) Controllable band alignment, excellent stability, strong redox ability High performance in both environmental and energy applications Limited interfacial flexibility, complex synthesis
Stimuli-responsive polymer-semiconductor composites Poly(N-isopropylacrylamide) (PNIPAM), poly(N-isopropylmethacrylamide) (PNIPMAM), polyacrylic acid (PAA), pH/redox-responsive polymers Condition-dependent, variable Moderate to high (dynamic tuning) Enhanced stability, self-regulation, improved recyclability Adaptive activity control, stable long-term performance Lower peak activity than static systems, complex design

3.1.1. Biological organic polymer-based composites

Biological polymer-semiconductor composites represent an emerging class of sustainable photocatalytic materials in which naturally derived polymers are integrated with semiconductor photocatalysts to improve photocatalytic efficiency, stability, and environmental compatibility. Unlike synthetic polymers, biological polymers are renewable, biodegradable, non-toxic, and rich in functional groups that can strongly interact with semiconductor surfaces. Common biological polymers used in photocatalytic composites are chitosan,52 cellulose,53 alginate,54 lignin,55 gelatin, silk fibroin, and various protein-based materials. These polymers serve not only as supporting matrices but also as active components that influence charge separation, surface adsorption, pollutant accessibility, and photocatalytic reaction pathways, as discussed in the mechanism section.56 Recent research has increasingly focused on biological polymer-semiconductor composites because they provide the advantages of green materials with enhanced photocatalytic performance, making them attractive for environmental remediation and sustainable energy applications.

Chitosan is one of the most extensively studied materials among other biological polymers due to its abundant amino (–NH2) and hydroxyl (–OH) groups in its structure. These functional groups provide strong coordination sites for semiconductor nanoparticles. Chitosan improves nanoparticle dispersion, prevents agglomeration, and increases the adsorption of pollutants through electrostatic interactions and chelation mechanisms.57 Therefore, chitosan-based composites exhibit higher degradation rates than pure semiconductors. However, chitosan possesses poor intrinsic electrical conductivity and limited light absorption capability. Therefore, its photocatalytic enhancement mainly arises from improved adsorption and interfacial interactions rather than direct participation in charge transport.58 Recent studies have addressed this limitation by combining chitosan with conductive carbon materials or conjugated polymers to create multifunctional photocatalytic systems.

Cellulose-based composites have also attracted significant attention because cellulose is the most abundant natural polymer on earth and possesses excellent mechanical stability, high surface area, and numerous hydroxyl groups. Cellulose functions as a robust support that improves the dispersion of semiconductor particles and increases the accessibility of photocatalytic active sites.59,60 Nanocellulose materials like cellulose nanofibers and cellulose nanocrystals provide particularly large surface areas and interconnected porous structures that facilitate pollutant diffusion and adsorption.61 Compared with conventional semiconductor powders, cellulose-supported photocatalysts generally demonstrate improved catalytic efficiency and recyclability. Similar to chitosan, cellulose is electronically insulated and contributes little to charge transport, which limits its ability to directly suppress electron–hole recombination.

Alginate-based semiconductor composites are another important category of biological photocatalysts. Alginate contains abundant carboxylate and hydroxyl groups that enable strong interactions with semiconductor surfaces and facilitate hydrogel formation. The porous hydrogel networks formed by alginate improve mass transfer, increase reactant accessibility, and simplify catalyst recovery after use. These characteristics make alginate particularly attractive for wastewater treatment applications.62,63 Nevertheless, the relatively low conductivity and limited photochemical activity of alginate restrict its direct contribution to charge separation processes.

Lignin-based photocatalytic composites have gained attention because lignin possesses aromatic and conjugated structures that distinguish it from most other biological polymers. Unlike cellulose and chitosan, lignin can actively participate in light absorption owing to its phenolic and aromatic functional groups. The π-conjugated structures within lignin facilitate electron transfer and can contribute to charge carrier migration when combined with semiconductors.64,65 Therefore, lignin-based composites show superior visible-light activity compared with cellulose- or starch-based systems. However, lignin suffers from structural complexity and variability depending on its source and extraction method, which makes reproducible photocatalyst design more challenging.

Protein-based polymers such as gelatin, collagen, silk fibroin, and bovine serum albumin have also been incorporated into semiconductor photocatalysts. These materials contain abundant amino acid residues that provide multiple functional groups for semiconductor immobilization and interfacial engineering. Protein-based composites display enhanced biocompatibility and structural flexibility.66 Particularly, silk fibroin has demonstrated excellent performance due to its ordered molecular structure and excellent mechanical properties. However, protein degradation under prolonged irradiation and harsh reaction conditions remains a significant challenge.

The influence of biological polymers can be understood through several key mechanisms. First, biological polymers improve the dispersion of semiconductor nanoparticles and suppress particle agglomeration. Therefore, they increase the effective surface area of composites.67 Second, their abundant functional groups enhance pollutant adsorption, which results in higher local concentrations of reactants near photocatalytic active sites.68 Third, porous polymer networks facilitate mass transfer and improve the accessibility of reactants and products.69 Fourth, certain biological polymers (particularly lignin and some protein-derived materials) can contribute to visible-light absorption and interfacial electron transfer.70 Collectively, these effects enhance photocatalytic performance even when the biological polymer itself is not photoactive. On the other hand, biological polymers generally exhibit weaker electronic properties than conjugated polymers, conducting polymers, and polymeric semiconductors. Conjugated polymers such as polythiophene and polyfluorene directly enhance visible-light absorption and charge transport through extended π-electron delocalization. Conducting polymers like polyaniline and polypyrrole efficiently suppress charge recombination due to their high electrical conductivity. Polymeric semiconductors like g-C3N4 actively participate in light harvesting and photocatalytic reactions. In contrast, most biological polymers primarily function as adsorption promoters, support matrices, and interfacial modifiers rather than active charge-transfer materials. Therefore, their enhancement of photocatalytic activity is indirect and generally less pronounced than that achieved by electronically active synthetic polymers. Biological polymers have several unique advantages that are increasingly valued in modern photocatalytic research. Their sustainability, biodegradability, low cost, and environmental compatibility align well with the principles of green chemistry and circular material design. Additionally, advances in bio-inspired material engineering, molecular functionalization, and hybrid composite synthesis are enabling biological polymers to play increasingly active roles in charge separation and photocatalytic reactions.71 Recent studies have demonstrated that integrating biological polymers with conductive materials, carbon nanostructures, or advanced heterojunction photocatalysts can overcome many of their traditional limitations while retaining their environmental benefits.

Biological polymer-semiconductor composites represent an attractive and rapidly developing research area. Although their photocatalytic enhancement mechanisms differ from those of conjugated and conducting polymers, they provide valuable advantages in adsorption, dispersion, stability, recyclability, and sustainability. Future research should focus on improving their electronic functionality, developing multifunctional hybrid systems, and establishing clear structure–property–performance relationships to fully exploit their potential in next-generation photocatalytic technologies.

3.1.2. Synthesized organic polymer-based composites

Organic polymers used in photocatalytic composites differ markedly in their electronic structures, charge-transport properties, stability, responsive behavior, and functional roles. These differences directly influence photocatalytic activity, reaction pathways, and long-term durability. Generally, polymers employed in photocatalysis can be categorized into conjugated polymers, conducting polymers, stimuli-responsive polymers, and polymeric semiconductors, each of which provides distinct advantages and limitations when integrated with inorganic semiconductors.

3.1.2.1. Conjugated polymers

Conjugated polymers possess extended π-electron systems arising from alternating single and double bonds along their backbone. This delocalized electronic structure allows for the efficient absorption of visible light and tunable optical band gaps through molecular design. By modifying the polymer backbone, side chains, or donor–acceptor segments, their HOMO–LUMO energy levels can be precisely adjusted to match the band structure of inorganic semiconductors.

In photocatalytic composites, conjugated polymers primarily function as photosensitizers and electron donors, which significantly extend light absorption into the visible region compared to bare inorganic photocatalysts. Upon illumination, photoexcited electrons in the polymer can be injected into the semiconductor conduction band, which enhances charge generation efficiency and hence increases reductive oxygen species (ROS). However, conjugated polymers generally exhibit moderate charge mobility and limited intrinsic catalytic activity. As a result, their photocatalytic performance strongly depends on effective interfacial coupling with semiconductors.48,51

Conjugated polymers typically provide better light-harvesting capability but weaker charge transport compared with conducting polymers. Relative to polymeric semiconductors, they introduce superior tunability but lower intrinsic stability under prolonged irradiation. Consequently, conjugated polymer-semiconductor composites show high initial photocatalytic activity but require careful structural optimization to ensure long-term durability.

3.1.2.2. Conducting polymers

Conducting polymers like polypyrrole, polyaniline, and polythiophene represent a subclass of conjugated polymers distinguished by their high electrical conductivity upon doping. Their ability to exist in multiple oxidation states enables efficient charge transport and storage, which makes them particularly effective in suppressing electron–hole recombination.

The conducting polymers act as charge-transport layers or electron sinks when coupled with inorganic semiconductors and hence facilitate rapid interfacial charge transfer. This property makes them effective in photocatalytic degradation reactions, where fast electron consumption by oxygen or pollutants is critical. In many cases, conducting polymer-based composites exhibit lower recombination rates and higher apparent reaction kinetics than conjugated polymer-based systems.72,73

Conducting polymers typically show weaker light absorption tunability and narrower absorption bands compared with conjugated polymers. Moreover, their chemical stability under strong oxidative photocatalytic conditions can be inferior, which leads to gradual performance decay. Relative to polymeric semiconductors, conducting polymers excel in charge management but lack intrinsic photocatalytic active sites. Therefore, their performance advantage lies mainly in charge separation rather than catalytic activity.

3.1.2.3. Polymeric semiconductors

Polymeric semiconductors like graphitic carbon nitride, covalent organic frameworks, and conjugated microporous polymers possess intrinsic semiconducting properties and well-defined band structures. Unlike conjugated and conducting polymers, these materials can act as active photocatalysts and directly participate in redox reactions rather than merely modifying charge dynamics.74,75

Their rigid frameworks, extended conjugation, and porous architectures result in improved chemical and photochemical stability. In photocatalytic composites, polymeric semiconductors frequently exhibit superior durability and sustained activity compared to conducting polymers. Moreover, their intrinsic catalytic sites and favorable band positions make them suitable for demanding reactions, such as hydrogen evolution76 and CO2 reduction.77

Polymeric semiconductors generally suffer from lower charge mobility and limited absorption intensity compared with conjugated polymers. As a result, their photocatalytic performance often relies on coupling with inorganic semiconductors or co-catalysts to enhance charge separation and reaction kinetics. In comparative terms, polymeric semiconductors are better conjugated and conducting polymers in stability but can underperform in visible-light absorption efficiency unless structurally engineered.

3.1.2.4. Stimuli-responsive organic polymers

Stimuli-responsive organic polymers represent an advanced class of materials in polymer-semiconductor composites, which introduce dynamic and reversible control over photocatalytic activity in response to external triggers, such as pH, temperature, light intensity, or redox environment. Unlike conventional polymer systems discussed in Sections 3.1.1–3.1.3, which primarily provide static improvements in light absorption, charge separation, or surface functionality, stimuli-responsive polymers introduce adaptive behavior that allows the photocatalytic system to self-regulate under changing reaction conditions. This responsiveness can significantly enhance reaction efficiency, selectivity, and operational stability, particularly in complex environmental and energy conversion processes.

Stimuli-responsive polymers show superior performance due to their ability to reversibly modify surface wettability, adsorption affinity, and charge accessibility compared to non-conjugated insulating polymers. Insulating polymers typically improve photocatalytic activity through enhanced dispersion, surface protection, or pollutant adsorption, but their lack of electronic conductivity limits charge-transport efficiency.78,79 In contrast, stimuli-responsive polymers can modulate interfacial interactions and charge transfer pathways in real time, which enables the improved utilization of photogenerated carriers. However, their more complex molecular design and synthesis can reduce scalability compared with simpler insulating polymer systems.

Stimuli-responsive polymers exhibit slightly lower intrinsic photocatalytic enhancement under steady-state conditions relative to conjugated polymers (which excel in visible-light absorption and charge delocalization). Conjugated polymers provide strong and continuous photosensitization and charge transport, which leads to consistently high photocatalytic activity.80–82 Nevertheless, stimuli-responsive polymers are better than conjugated polymers in environments in which reaction conditions fluctuate due to their adaptive behavior, which minimizes deactivation, fouling, or undesired side reactions. This makes stimuli-responsive systems advantageous for long-term or cyclic photocatalytic applications.

Stimuli-responsive polymers provide a broader functional scope by coupling charge regulation with environmental responsiveness compared with conducting polymers, which primarily enhance photocatalytic performance through improved electrical conductivity and interfacial charge transfer. Conducting polymers efficiently suppress recombination and facilitate electron transport, which results in high reaction rates. However, they suffer from structural degradation or over-oxidation under prolonged illumination. Stimuli-responsive polymers mitigate these issues by dynamically adjusting their conformation or electronic properties and hence enhancing durability and photocatalytic stability.82

Stimuli-responsive polymer-semiconductor composites occupy a unique position among polymer-based photocatalysts. They cannot always surpass conjugated or conducting polymers in terms of maximum reaction rates, and their ability to adapt to environmental changes provides superior operational robustness, selectivity, and recyclability. This adaptive functionality becomes particularly valuable in real-world photocatalytic systems, where fluctuating conditions limit the performance of static polymer-semiconductor composites. Consequently, stimuli-responsive polymers represent a favorable direction for next-generation photocatalytic materials, complementing the strengths of the polymer classes discussed in these polymers (Sections 3.1.1–3.1.3). In the present study, very limited research has been reported on such systems, and more research is required in the future.

Conjugated polymers excel in visible-light harvesting, conducting polymers dominate charge transport and recombination suppression, polymeric semiconductors provide intrinsic catalytic activity and stability, and stimuli-responsive polymers show dynamic performance under different reaction conditions, which provide selectivity, recyclability, and operational robustness. No single polymer class is universally superior, and optimal photocatalytic performance arises from the strategic selection and integration of polymer types based on application requirements.

For pollutant degradation, conducting polymer-semiconductor composites show faster reaction rates due to efficient charge separation. In contrast, hydrogen evolution and CO2 reduction reactions benefit more from polymeric semiconductor-based systems owing to their stronger redox capability and stability. Conjugated polymers serve as powerful sensitizers in systems where light utilization is the primary limitation. Stimuli-responsive polymer-based composites provide stability, selectivity, and recyclability due to their responsive behavior under different stimulus conditions.

3.2. Interaction mechanisms

The interaction mechanism between organic polymers and inorganic semiconductors is a decisive factor governing the extent to which polymer incorporation enhances photocatalytic activity. The intrinsic properties of polymers define their potential roles in light absorption or charge transport. The nature of their interaction with the semiconductor ultimately determines the charge transfer efficiency, carrier lifetime, and catalyst stability. Different interaction modes (ranging from weak physical adsorption to strong chemical bonding) result in distinct levels of photocatalytic enhancement as well as different challenges that must be tackled through rational composite architecture.83

The simplest form of interaction arises from physical adsorption through van der Waals forces or electrostatic attraction. In such systems, polymers are deposited or coated onto semiconductor surfaces without forming strong chemical bonds. These physically adsorbed polymers can significantly enhance photocatalytic activity by improving visible-light absorption and increasing surface affinity toward reactant molecules. For example, conjugated polymers physically coupled with wide-band-gap semiconductors extend light absorption into the visible region, which results in a higher photocatalytic response under solar irradiation. Nevertheless, the charge transfer across the polymer-semiconductor boundary is inefficient because electronic coupling at the interface is weak. As a result, the enhancement in photocatalytic activity is usually moderate and primarily limited to light-harvesting effects rather than effective charge separation.84–86

In addition to the limited charge transfer efficiency, physically adsorbed polymers can suffer from poor interfacial stability. During prolonged photocatalytic reactions (especially in aqueous or oxidative environments), polymers can detach from the semiconductor surface, which leads to gradual performance degradation. This challenge highlights the need for stronger interfacial interactions that can maintain structural integrity while facilitating charge migration. To address this limitation, researchers have introduced secondary interactions such as hydrogen bonding or π–π stacking to reinforce polymer attachment and improve electronic communication across the interface.

Hydrogen bonding and π–π interactions represent an intermediate interaction regime that provides a balance between synthetic simplicity and performance enhancement. Hydrogen bonds are formed between functional groups on polymers (such as amine, hydroxyl, or carboxyl groups) and surface hydroxyls on semiconductors, while π–π interactions arise between aromatic polymer backbones and π-conjugated semiconductor surfaces. These interactions improve interfacial contact and reduce charge transfer resistance compared with purely physical adsorption. As a result, composites stabilized by hydrogen bonding or π–π stacking exhibit more efficient charge separation and higher photocatalytic activity. Nevertheless, these interactions remain non-covalent in nature and can weaken under harsh reaction conditions, such as prolonged irradiation or extreme pH environments.87,88

Covalent bonding between polymers and semiconductors has been widely explored to overcome the stability limitations of non-covalent interactions. Covalently bonded composites provide the strongest interfacial electronic coupling, which enables direct and rapid charge transfer across the interface. This strong coupling significantly suppresses electron–hole recombination and leads to a substantial enhancement in photocatalytic activity.89 In many cases, covalently grafted polymers act as efficient charge extraction layers that promote directional charge flow and improve quantum efficiency. Covalently bonded composites demonstrate superior photocatalytic performance and long-term stability compared with physically or hydrogen-bonded systems.

Covalent polymer-semiconductor composites introduce new challenges related to synthesis complexity and structural rigidity. Strong chemical bonding can alter semiconductor surface states or reduce flexibility for post-synthesis modification.90 Additionally, excessive polymer coverage can block active sites and hinder mass transfer. These issues can be resolved by employing controlled surface functionalization strategies, like surface-initiated polymerization or mild coupling reactions, that preserve semiconductor activity while maintaining strong interfacial coupling.

Another important interaction mechanism involves coordination bonding between polymer functional groups and surface metal sites on semiconductors.91–93 In such systems, polymers coordinate with metal ions or surface atoms, which form localized charge transfer centers that facilitate electron migration. Coordination interactions generally provide stronger binding and better charge transfer than physical adsorption but can be less stable than covalent bonding under photocatalytic conditions. Metal leaching or competitive adsorption by reactants can weaken coordination bonds, thereby reducing long-term performance. Designing polymers with multidentate or chelating groups provides an effective solution to enhance coordination stability and durability.

The extent of photocatalytic enhancement follows a clear trend dictated by the interfacial interaction strength. Covalently bonded composites deliver the highest activity enhancement due to efficient charge separation and prolonged carrier lifetimes, followed by coordination and π–π/hydrogen-bonded systems, while physically adsorbed polymers provide the least enhancement. However, stronger interactions are accompanied by increased synthesis complexity and potential trade-offs in surface accessibility. Therefore, the optimal interaction mechanism depends on the target application and the specific limitations of the semiconductor.

Organic polymer-semiconductor interactions directly address several intrinsic shortcomings of conventional photocatalysts. Polymer sensitization compensates for poor visible-light absorption, interfacial coupling suppresses rapid charge recombination, and polymer coatings protect semiconductors from photocorrosion. At the same time, challenges such as polymer degradation, interface instability, and blocked active sites must be carefully managed through rational material design. Achieving a balance between strong interfacial coupling and preserved catalytic functionality remains a central challenge in this field.

Interaction mechanisms between polymers and semiconductors are not structural features but active determinants of photocatalytic performance. A clear understanding of how different interaction modes influence charge dynamics, stability, and surface reactivity is essential for designing high-performance polymer-semiconductor photocatalysts. These interfacial considerations form a critical foundation for the activity tuning strategies discussed in the subsequent section (Table 2).

Table 2. Comparison between interaction mechanisms of polymer-semiconductor photocatalytic composites.

Interaction mechanism Nature of interaction Polymers Interfacial strength Advantages Photocatalytic activity Challenges
Physical adsorption (van der Waals forces) Weak, non-specific surface interactions Polyvinyl alcohol (PVA), polyethylene glycol (PEG), poly(methyl methacrylate) (PMMA) Low Simple fabrication; minimal structural disruption Slight enhancement due to better dispersion Poor interfacial stability; weak charge separation
Electrostatic interactions Coulombic attraction between oppositely charged species Polyelectrolytes, chitosan Moderate Tunable through pH or ionic strength Moderate enhancement under specific pH conditions Reversible binding, sensitive to reaction environment
Hydrogen bonding Directional non-covalent bonding Cellulose derivatives, PAA, PVA Moderate Improves interfacial contact and stability Significant improvement in photocatalytic rates Temperature-sensitive, weak under harsh conditions
π–π stacking interactions Aromatic ring overlap Polythiophene, g-C3N4 Moderate to high Enhances electron mobility and light absorption High visible-light photocatalytic activity Requires conjugated polymer structures
Covalent bonding Strong chemical linkage Functionalized polymers, COFs Very high Excellent stability; minimized recombination Substantial and durable activity enhancement Complex synthesis; risk of defect formation
Donor–acceptor (D–A) interactions Electronic charge redistribution at the interface D–A polymers, conjugated copolymers High Efficient separation, strong redox capability Superior performance (Z-/S-scheme) Requires precise energy-level matching

4. Factors governing photocatalytic activity

Polymers control the photocatalytic performance of polymer-semiconductor composites in various ways.

4.1. Nature of polymers

The type of organic polymer incorporated into polymer-semiconductor composites plays a central role in their photocatalytic performance because it determines whether the polymer functions merely as a structural modifier or actively participates in light harvesting and charge transport. Based on their electronic properties, polymers used in photocatalytic composites are generally categorized into different types, as discussed in Section 3. Each polymer contributes differently to the activity enhancement of the composites. This point is discussed in detail in Section 3. Therefore, there is no need for a detailed discussion of this point.94–96

The polymer type dictates the fundamental role of the polymer in photocatalytic composites. Although non-conjugated polymers primarily enhance stability and surface properties, conjugated and conducting polymers actively improve light absorption and charge separation. Responsive polymers also improve the light adsorption, selectivity, stability, and diffusion rate of the reactant to the surface of the semiconductor. Conducting polymers generally provide the highest activity enhancement although their long-term durability must be carefully addressed. This comparison underscores polymer type as a primary tuning parameter for optimizing photocatalytic activity, which forms the foundation for the subsequent activity-governing factors discussed in the following sections.

4.2. Chemical structure of polymers

Functional group variation is a critical determinant of photocatalytic performance in polymer-semiconductor composites, as functional moieties directly govern interfacial bonding strength, charge transfer efficiency, surface adsorption behavior, stimuli-responsive behavior, and chemical stability. Different functional groups introduce distinct electronic and chemical environments at the polymer-semiconductor interface, which lead to hierarchical effects on photocatalytic activity.

Electron-donating functional groups such as amines (–NH2 and –NH–) and hydroxyls (–OH) play a dominant role in enhancing photocatalytic efficiency by facilitating strong interfacial interactions and promoting charge transfer. Amine groups act as electron-rich sites that coordinate with metal centers in semiconductors, which form robust donor–acceptor interfaces. This interaction lowers interfacial resistance and accelerates electron extraction from the semiconductor, effectively suppressing charge recombination. As a result, amine-functionalized polymers are generally better than their hydroxyl-functionalized counterparts in visible-light-driven photocatalysis, especially in hydrogen evolution and reduction reactions.97

Hydroxyl groups contribute primarily through hydrogen bonding and improved surface wettability, which enhances the adsorption of polar reactants and facilitates interfacial contact. Hydroxyl-rich polymers improve photocatalytic reaction kinetics through enhanced mass transport, whose impact on electronic charge transfer is weaker than that of amine-containing polymers. Consequently, hydroxyl-functionalized systems show moderate activity enhancement but superior stability and recyclability.

Electron-withdrawing functional groups such as carboxyl (–COOH), sulfonic (–SO3H), and carbonyl (–C Created by potrace 1.16, written by Peter Selinger 2001-2019 O) groups introduce additional hierarchies in functional performance. These groups enhance the surface acidity and adsorption of cationic species, which improve the photocatalytic degradation of dyes and pollutants. Carboxyl groups can also form coordination bonds with semiconductor surfaces, which improve interfacial stability. However, excessive electron-withdrawing characteristics can reduce charge mobility within the polymer and impede electron transfer, which leads to lower activity in reduction-dominated reactions. Thus, polymers with balanced donor–acceptor functionalization are superior to those dominated by strongly withdrawing groups.98,99

The acidic (–COOH) and basic (–NH2) groups also make the composite for pH responsive behavior. These groups have the ability to accept (basic (vNH2) group) and donate (acidic (–COOH) group) the proton from or to the medium. The –NH2 groups shift into –NH3+ after accepting the proton (at pH ≤ pKb value). Therefore, electrostatic repulsion takes place, which results in an increase in the porous size and hence increases the diffusion rate of the reactant from the medium to the surface of the semiconductors. On the other hand, the porous size of the composite decreases with increasing pH of the medium (at pH ≥ pKb). Similarly, the porous size can be altered by changing the pH of the medium in an acidic (–COOH) group containing polymer-semiconductor composites.100 These composites deswell at low pH (pH ≤ pKa) and swell at high pH (pH ≥ pKa) due to the creation of the same negative charge in the structure at a high pH. Under these conditions, these functional groups also affect interfacial stability due to the availability of electrons.101

A functional hierarchy emerges when multiple functional groups coexist within the same polymer chain. In such systems, electron-donating groups primarily regulate charge transfer and recombination suppression, while electron-withdrawing groups control adsorption selectivity and interfacial stability. For example, polymers containing both amine and carboxyl groups exhibit synergistic behavior that combines efficient charge separation with strong reactant adsorption. This hierarchical functional arrangement results in superior photocatalytic performance compared with single-function polymers, particularly in complex environmental matrices.

Functional group variation establishes a hierarchy of photocatalytic roles, where electron-donating groups dominate charge transfer enhancement, acidic and basic groups control the pH-responsive behavior, which produces high selectivity, polar groups govern adsorption and wettability, and electron-withdrawing groups stabilize interfaces and tune selectivity. Therefore, rational design of polymer chemical structure through controlled functional group incorporation and hierarchical organization is a powerful strategy for tuning photocatalytic activity. This functional hierarchy directly links polymer chemistry to interfacial charge transfer mechanisms discussed in Section 3.2 and to application-specific performance trends outlined in Section 5.

4.3. Band gap engineering

Band gap engineering is a fundamental approach for tuning the photocatalytic activity of organic polymer-semiconductor composites, as it directly controls light absorption capability and solar energy utilization. Many conventional semiconductors possess wide band gaps that restrict their photoresponse to the ultraviolet region and limit overall efficiency under natural sunlight. Incorporation of organic polymers (particularly temperature or photon responsive, conjugated and conducting polymers) enables effective modulation of the composite band gap, which extends absorption into the visible region and enhances photocatalytic performance.

Organic polymers offer exceptional flexibility in band gap tuning through molecular design strategies, such as adjustment of conjugation length, donor–acceptor architecture, and functional group substitution. Extended π-conjugation lowers the polymer band gap and broadens the absorption spectrum, while donor–acceptor polymers introduce intramolecular charge transfer states that further enhance visible-light harvesting. Polymer-modified systems exhibit significantly improved photon absorption and higher densities of photogenerated charge carriers compared with bare semiconductors, which lead to increased photocatalytic reaction rates.102–104

Band gap engineering must be carefully controlled to avoid adverse effects. Excessive band gap narrowing or uncontrolled polymer loading can introduce defect states or mid-gap energy levels that act as recombination centers, counteracting the benefits of enhanced light absorption. Poorly ordered polymer structures can also impede charge transport, which reduces the effective utilization of absorbed photons. Therefore, optimal band gap engineering requires a balance of the light absorption enhancement with efficient charge separation and transport.105–107

Effective band gap engineering in polymer-semiconductor composites enhances visible-light absorption while maintaining a favorable electronic structure for photocatalysis. These composites consistently outperform pristine semiconductors in environmental and energy applications when properly designed. This section establishes the foundation for the energy-level alignment and interfacial charge transfer mechanisms discussed in subsequent sections, which emphasize band gap engineering as a primary tuning parameter for high-performance photocatalytic systems.

4.4. Energy-level alignment

Energy-level alignment between organic polymers and semiconductors is a decisive factor governing the efficiency of photocatalytic processes in polymer-semiconductor composites. Although band gap engineering determines the range of light absorption, proper alignment of the highest occupied molecular orbital (HOMO) and lowest unoccupied molecular orbital (LUMO) of polymers with the valence band (VB) and conduction band (CB) of semiconductors dictates the direction, driving force, and efficiency of interfacial charge transfer.

Favorable energy-level alignment enables the rapid separation of photogenerated charge carriers and suppresses recombination, which leads to enhanced photocatalytic activity.

In polymer-semiconductor composites, polymers can function either as electron donors or acceptors depending on their electronic structure. When the LUMO level of the polymer lies above the semiconductor CB, photogenerated electrons can be efficiently injected from the polymer into the semiconductor, which promotes reduction reactions, such as hydrogen evolution or CO2 conversion. Conversely, polymers with deeper HOMO levels than the semiconductor VB facilitate hole extraction, which enhances oxidation reactions and reduces photocorrosion. Compared with bare semiconductors or poorly matched composites, systems with optimized energy-level alignment exhibit faster interfacial charge transfer and higher quantum efficiencies.86,108–110

Energy-level alignment also plays a crucial role in determining reaction selectivity and operational stability. Proper alignment prevents back-electron transfer and charge accumulation at the interface, which can otherwise lead to recombination or photodegradation. In contrast, mismatched energy levels create energy barriers that trap charge carriers and negate the advantages of improved light absorption. Comparative studies consistently show that polymer-semiconductor composites with rationally engineered energy alignment are better than those with similar band gaps but inferior interfacial matching. Bhankhar et al.49 used Li-doped NiO-polyaniline (LDN-PAn) composite for the degradation of MB. They reported the energy level alignment of the HOMO–LUMO of PAn with the CB–VB of LDN. The bandgap energy of LDN was 2.90 eV, but its photocatalytic activity was lower than that of PAn (bandgap energy = 3.16 eV), as shown in Fig. 4. The reason behind this is electron/hole recombination at a lower bandgap energy. This recombination of electrons and holes was reduced to a composite form. They reported that as the content of LDN increased in the composite during synthesis, the bandgap energy of the composite was reduced with better alignment of energy levels, which reduced the electron/hole recombination. Therefore, the photocatalytic efficiency of the composite increased as the content of LDN in the composites increased.

Fig. 4. Photocatalytic degradation efficiency at different compositions of the composite, resulting in various band gap values.49Fig. 4 adapted from ref. 49 with permission from Wiley, copyright 2026.

Fig. 4

Energy-level alignment serves as an electronic bridge that translates enhanced light absorption into effective photocatalytic reactions. Its optimization (in conjunction with band gap engineering) is essential for maximizing the performance of polymer-semiconductor composites. This section directly connects to the interfacial charge transfer mechanisms discussed in the subsequent section, which highlights energy-level alignment as a critical tuning parameter for efficient and durable photocatalysis.

4.5. Interfacial charge transfer mechanisms

Interfacial charge transfer is a decisive process that influences the photocatalytic efficiency of organic polymer-semiconductor composites because it directly controls the separation, migration, and utilization of photogenerated charge carriers. Light absorption and energy-level alignment determine the generation of excited electrons and holes. The efficiency of charge transfer across the polymer-semiconductor interface dictates whether these carriers participate in surface redox reactions or undergo recombination. Therefore, understanding interfacial charge transfer mechanisms is essential for translating structural and electronic advantages into practical photocatalytic performance.

In polymer-semiconductor composites, charge transfer typically occurs through photoinduced electron or hole migration driven by interfacial potential differences. Upon illumination, charge carriers can be generated in the semiconductor, the polymer, or both components, which depend on their respective absorption characteristics. Efficient charge transfer requires intimate interfacial contact and favorable energetic alignment. When these conditions are met, electrons can be transferred from the excited polymer to the semiconductor CB or from the semiconductor to the polymer depending on the system design. This directional charge migration separates electrons and holes and hence suppresses recombination.111,112

Different charge transfer pathways result in distinct photocatalytic behaviors, as discussed in Section 2. In type-II heterojunction systems, electrons and holes migrate to different materials that reduce recombination but are often at the expense of redox potential. Although this configuration improves charge separation compared to bare semiconductors, it can limit the reaction driving force in demanding applications. In contrast, Z-scheme and S-scheme charge transfer mechanisms are enabled by precise energy-level alignment and strong interfacial coupling, preserving high redox ability while maintaining effective charge separation. Polymer-based composites have demonstrated particular advantages in forming such architectures due to the tunability of polymer energy levels.

The nature of the polymer-semiconductor interaction strongly influences interfacial charge transfer efficiency. As discussed in Section 3.2, covalent or coordination bonding typically provides lower charge transfer resistance and more efficient carrier migration than weak physical adsorption. Strongly coupled interfaces facilitate rapid electron extraction and prolong carrier lifetimes, leading to higher photocatalytic activity. However, excessive interfacial coupling or dense polymer layers can introduce charge trapping sites or hinder reactant diffusion, which highlights the importance of controlled interface engineering.

Charge transfer dynamics are also influenced by polymer conductivity and molecular ordering. Conducting polymers generally enable faster interfacial charge transport than non-conducting polymers due to higher carrier mobility along the polymer backbone.113 Well-ordered polymer domains facilitate directional charge flow, whereas disordered polymer structures can introduce energetic disorder that increases recombination probability. Compared with conventional inorganic heterojunctions, polymer-semiconductor interfaces offer greater flexibility in tuning charge-transport pathways but require careful molecular design to avoid disorder-induced losses.

Polymer-semiconductor interfaces can also introduce challenges such as interfacial defects, charge trapping, and long-term instability. Photogenerated charges can accumulate at poorly defined interfaces, which leads to recombination or polymer degradation. These issues can be mitigated through optimized synthesis strategies, surface functionalization, and controlled polymer loading, which enhance interfacial uniformity and electronic coupling. Additionally, incorporating protective polymer layers can suppress the photocorrosion of sensitive semiconductors while maintaining efficient charge transfer.

Nayab et al.114 reported the synthesis of iodine-doped manganese oxide-polythiophene (I–MnO2-PTh) and used it as a photocatalyst for the degradation of rhodamine-B (RhB). PTh has a very low bandgap energy (2 eV). The electron of the HOMO of PTh absorbs light and shifts into the LUMO while leaving holes behind, as shown in Fig. 5. The CB of MnO2 was lower in energy than the LUMO of PTh. The photogenerated electrons of LUMO shift into the CB of MnO2. This shifting of electrons increases the reduction of oxygen molecules into peroxide radicals (˙O2−) and hence increases the degradation of RhB. The holes generated in the HOMO of PTh oxidize the water molecules into hydroxyl radicals (˙OH), which results in an increased degradation rate. They showed 95% degradation of RhB with polymer composites.

Fig. 5. Photocatalytic degradation mechanism of RhB by I–MnO2/PTh.114Fig. 5 adapted from ref. 114 with permission from Springer, copyright 2026.

Fig. 5

Polymer-modified photocatalysts are consistently better than bare semiconductors in charge separation efficiency owing to the presence of tailored interfacial charge transfer pathways. However, their performance advantage depends critically on interface quality and energetic alignment. Systems with optimized interfacial charge transfer mechanisms exhibit significantly higher quantum efficiencies and reaction rates, while poorly engineered interfaces can negate the benefits of polymer incorporation.

Interfacial charge transfer mechanisms serve as the functional bridge between light absorption and surface catalysis in organic polymer-semiconductor composites. Effective tuning of these mechanisms through molecular design, interface engineering, and synthesis control is essential for achieving high photocatalytic efficiency. These considerations provide a foundation for understanding how morphology and surface properties further influence photocatalytic activity, as discussed in the following subsection.

4.6. Morphology

Morphology is a critical structural parameter that governs photocatalytic activity in organic polymer-semiconductor composites by influencing light absorption, charge-transport pathways, and the accessibility of reactive sites. Unlike conventional bulk photocatalysts, polymer-semiconductor composites show remarkable flexibility in morphological design due to the processability of polymers and their ability to guide nanostructure formation. As a result, morphological control has emerged as an effective strategy to enhance photocatalytic efficiency beyond what can be achieved through electronic tuning alone.

Nanostructured morphologies such as one-dimensional nanofibers, two-dimensional nanosheets, and three-dimensional hierarchical architectures generally exhibit better performance than irregular or bulk structures. These morphologies shorten charge diffusion distances and promote the efficient separation of photogenerated carriers by enabling rapid transport to reactive interfaces. For instance, polymer-directed nanosheets or nanofiber composites facilitate directional charge migration along extended interfaces and hence reduce bulk recombination losses, which are commonly observed in conventional photocatalysts.115–117

Core-shell and layered heterostructures represent particularly effective morphological designs for polymer-semiconductor composites. In such architectures, the intimate interfacial contact between the polymer and semiconductor ensures efficient charge transfer while spatially separating oxidation and reduction sites. Compared with physically mixed composites, core–shell structures exhibit higher photocatalytic activity due to minimized interfacial resistance and improved charge utilization (one author has already been reported that how can effect the core–shell morphology during performance).118 However, excessively thick polymer shells can hinder light penetration and block active semiconductor sites, which indicates the importance of precise thickness control of the polymer around semiconductors.119,120

Hierarchical morphologies combining micro-, meso-, and nanoscale features further enhance photocatalytic performance by integrating multiple advantages. These structures improve light scattering, increase interfacial area, and facilitate mass transport simultaneously. Polymer templates and self-assembly strategies enable the formation of such complex architectures, which are difficult to achieve in purely inorganic systems. Compared with flat or densely packed structures, hierarchical morphologies consistently demonstrate higher reaction rates and improved stability.121–123

Morphological optimization introduces challenges related to structural stability and reproducibility. Highly porous or loosely assembled structures can collapse during prolonged photocatalytic operation, which leads to performance degradation. Additionally, complex morphologies require sophisticated synthesis protocols that can limit scalability. These challenges can be addressed by reinforcing polymer frameworks that optimize crosslinking density and adopt scalable fabrication methods.

Morphology serves as a main activity-tuning parameter that mediates the relationship between material structure and photocatalytic performance. Rational morphological design enables efficient charge transport, enhanced light utilization, and improved surface reactivity. When combined with optimized polymer chemistry and interfacial charge transfer mechanisms, morphological control significantly elevates the performance of organic polymer-semiconductor photocatalysts.

4.7. Surface area

Surface area is a fundamental factor influencing photocatalytic activity in organic polymer-semiconductor composites because it directly determines the number of accessible active sites available for adsorption and surface redox reactions. Polymer-modified photocatalysts exhibit significantly higher effective surface areas due to improved particle dispersion and the prevention of agglomeration compared with conventional bulk semiconductors. This increase in surface area enhances contact between the photocatalyst and reactant molecules and hence accelerates reaction kinetics.

The incorporation of organic polymers can improve surface area through several mechanisms, such as templating effects, steric stabilization, and formation of nanostructured or porous frameworks. Conjugated and conducting polymers (when uniformly distributed) can prevent semiconductor nanoparticles from sintering or clustering, which preserves high surface exposure. As a result, polymer-semiconductor composites generally outperform pristine semiconductors with lower surface areas in photocatalytic degradation and energy conversion reactions.124–126

Surface area enhancement must be carefully optimized because excessive polymer coverage can have adverse effects. Thick polymer layers can block active semiconductor sites, reduce light penetration and hinder interfacial charge transfer. In such cases, a high surface area does not translate into improved photocatalytic activity. Compared with conventional photocatalysts, polymer-semiconductor systems require more precise control over the surface area to ensure that increased exposure is coupled with efficient electronic communication and charge utilization.127

Moderate increases in surface area combined with strong interfacial charge transfer yield higher photocatalytic performance than systems with maximal surface area but poor charge separation. This observation underscores that surface area is a necessary but not sufficient condition for high activity. The most effective polymer-semiconductor composites balance surface exposure with optimized energy-level alignment and interfacial coupling.

Tanuj et al.34 synthesized Nb-doped ZnO (NDZ) with and without polyvinyl acetate (PVAc). The value of the surface area increases from 5 m2 g−1 (5% NDZ) and 4 m2 g−1 (10% NDZ) to 28 m2 g−1 (5% NDZ-PVAc) and 17 m2 g−1 (10% NDZ-PVAc) for corresponding NDZ-PVAc composites, respectively. Polymer components do not show photocatalytic activity here but increase the adsorption capacity. In this way, its polymer facilitates approaching the pollutant to the surface of the NDZ. The greater the surface area, the more pollutants can reach the NDZ. Therefore, the greater the surface area, the more molecules of pollutants can reach the NDZ surface. The degradation efficiency of NDZ-PVAc increased against bisphenol A (BPA) and bromothymol blue (BTB) by 92% and 90%, respectively, under UV irradiation.

The surface area also plays an indirect role in enhancing photocatalyst stability and recyclability. Increased surface exposure facilitates a more uniform distribution of photogenerated charges, which reduces localized charge accumulation that can lead to photocorrosion. Polymer-induced stabilization of the surface area further contributes to long-term performance retention compared with bare semiconductors. The surface area is a critical structural parameter that enhances photocatalytic activity when synergistically integrated with polymer chemistry and interfacial charge transfer mechanisms. Rational surface area optimization (rather than maximization alone) is essential for achieving high-performance organic polymer-semiconductor photocatalysts.

4.8. Porosity

Porosity is a critical structural feature that governs mass transport, reactant diffusion, and product desorption in polymer-semiconductor photocatalysts. Although surface area determines the number of active sites, porosity controls how effectively reactants reach those sites and how efficiently products are removed. This directly impacts the overall photocatalytic efficiency of composites. Organic polymer incorporation induces micro-, meso-, or hierarchical porosity, which generates interconnected channels that facilitate molecular diffusion and enhance the accessibility of reactive sites compared with conventional dense photocatalysts.

Mesoporous and hierarchically porous structures are particularly effective because they balance a high surface area with efficient diffusion pathways. Microporous systems (although providing a high number of active sites per unit volume) can restrict the transport of larger reactant molecules or gases, which leads to diffusion-limited performance. By contrast, meso- and macro-porous architectures allow faster penetration of reactants and egress of products, resulting in higher reaction rates and improved utilization of photogenerated carriers.116,128,129 Polymer templating, self-assembly, and phase-separation methods are commonly employed to introduce controlled porosity in polymer-semiconductor composites.

The presence of porosity also influences light absorption and charge separation. Porous architecture enhances light scattering and increases the effective optical path length within the photocatalyst, which improves photon utilization. Furthermore, interconnected pores ensure that photogenerated charges can reach reactive interfaces more efficiently, which reduces recombination losses.130 Compared with non-porous semiconductors, polymer-semiconductor composites with well-engineered porosity consistently demonstrate superior photocatalytic performance in pollutant degradation,131 hydrogen evolution,132 and CO2 reduction.

Excessive porosity or loosely connected pore networks can compromise mechanical integrity and long-term stability, particularly under continuous photocatalytic operations. Collapsing pores can block diffusion pathways and reduce active site accessibility. Therefore, careful control of polymer content, crosslinking density, and structural reinforcement is essential to maintain both porosity and stability. Compared with conventional dense photocatalysts, polymer-semiconductor composites show superior tunability of porosity but require an optimized design to prevent structural degradation. Porosity plays a pivotal role in mediating mass transport, light utilization, and charge carrier accessibility in polymer-semiconductor photocatalysts. When synergistically combined with optimized morphology, surface area, and interfacial charge transfer, controlled porosity significantly enhances photocatalytic efficiency, which makes it a key design parameter in activity tuning strategies.

4.9. Composite synthesis strategies

The synthesis strategy of polymer-semiconductor composites is a key determinant of their photocatalytic performance. It dictates polymer distribution, interfacial contact, morphology, porosity, and, ultimately, charge transfer efficiency. Unlike conventional inorganic photocatalysts (whose properties are largely fixed by their crystal structure), polymer-semiconductor composites provide remarkable tunability through diverse fabrication approaches. Selecting an appropriate synthesis method allows for precise control over interfacial interactions, morphology, and functional group orientation, all of which directly influence photocatalytic activity.

In situ polymerization is one of the most widely employed strategies for fabricating polymer-semiconductor composites. In this approach, monomers are polymerized in the presence of semiconductor nanoparticles, which ensure intimate interfacial contact and uniform polymer coating. This method facilitates strong electronic coupling between the polymer and semiconductor, which is essential for efficient interfacial charge transfer. Compared with post-synthesis physical mixing, in situ polymerization consistently yields composites with higher photocatalytic activity due to improved charge separation and structural homogeneity. However, precise control oared polymerization conditions is required to avoid excessive polymer coverage that can hinder light absorption or block active sites. Lad et al.133 synthesized polypyrrole-copper oxide–nickel oxide (PPy-CuO–NiO) composites via an in situ oxidation process. They showed that the synthesized composites had excellent charge transfer capacity and stability.

Surface grafting or covalent anchoring of polymers onto semiconductor surfaces provides another effective route to high-performance composites. This strategy forms strong chemical bonds at the interface, which promote rapid charge transfer and long-term stability.116 Covalent grafting is particularly advantageous for systems where maintaining interfacial integrity under harsh reaction conditions is critical, such as photocatalytic water splitting or pollutant degradation.134 The main challenge lies in the complexity of functionalizing semiconductor surfaces and controlling grafting density, which can affect both the electronic properties and accessibility of active sites.

Self-assembly and template-assisted strategies exploit the intrinsic ordering tendencies of polymers and semiconductors to generate hierarchical structures with controlled morphology and porosity.135 These methods enable the formation of core–shell architectures, nanofibers, and layered heterojunctions, which have advantages in morphology, surface area, and diffusion pathways, as discussed in Sections 4.4–4.6. Compared with conventional mixing, self-assembly approaches provide superior light harvesting and mass transport though they require careful solvent selection, polymer design, and thermal or chemical processing to achieve reproducible structures.

Physical mixing or solution blending remains a simple and scalable method.134 It generally produces weaker interfacial interactions and less uniform polymer distribution. Such composites can still improve light absorption and surface adsorption compared with bare semiconductors. They suffer from limited charge transfer efficiency. Nevertheless, physical blending is suitable for preliminary screening of polymer-semiconductor combinations or for large-scale applications where cost and scalability are critical considerations.

Hydrothermal and solvothermal synthesis methods are also frequently employed to integrate polymers with semiconductors under controlled temperature and pressure conditions.136 These methods allow simultaneous control of morphology, crystallinity, and polymer distribution, which yield composites with enhanced interfacial contact and hierarchical structures. Compared with conventional solution-based methods, hydrothermal synthesis produces more robust and well-defined composites though it can involve longer processing times and higher energy input.

Along with these methods, the mixing composition ratio of semiconductors and polymers is also an important factor in determining the photocatalytic activity of the composites. The semiconductor facilitates the photocatalytic reaction by absorbing light, while the polymer facilitates the stabilization of the electrons and holes along with the transport of reactant molecules to the surface of the semiconductors. In this way, photocatalytic performance is enhanced by increasing the content of the semiconductor in the composite during synthesis up to a specific level. Photocatalytic activity decreases with an increase in the concentration of the semiconductors in the composites due to agglomeration (which decreases the surface area) or binding with the active sites of polymers, which are responsible for facilitating the transport of the reactant molecules to the surface of semiconductors. In this way, the performance of composites decreases by increasing the concentration of semiconductors in the composites after a specific level. Omer et al.137 synthesized polypyrrole-zinc ferrite–magnetite (PPy-ZnFe2O4–Fe3O4) composites and applied them for the removal of azithromycin (AM) from an aqueous medium. They increased the content of ZnFe2O4–Fe3O4 (0.0–1.25 g) and kept the content of PPy (2.5 g) constant to form a composite. They reported that the removal percentage increased initially from 43% to 76% as the content of ZnFe2O4–Fe3O4 increased from 0 to 0.75 g and decreased from 76% to 69% as the content of ZnFe2O4–Fe3O4 increased from 0.75 g to 1.25 g, as shown in Fig. 6. This decreasing trend was obtained due to the agglomeration and interaction of ferrite with the active sites of PPy, which reduced the approach of AM to the surface of the metal oxide.

Fig. 6. Percentage removal efficiency of the ZnFe2O4–Fe3O4-PPy composite against AM.137Fig. 6 adapted from ref. 137 with permission from the Eurasian Science Society, copyright 2025.

Fig. 6

The choice of synthesis strategies profoundly influences the structural, electronic, and interfacial properties of polymer-semiconductor composites. Methods enabling strong interfacial coupling, controlled morphology, and uniform polymer distribution (like in situ polymerization, covalent grafting, and self-assembly) generally result in higher photocatalytic activity than simple physical mixing. However, synthesis complexity, scalability, and reproducibility remain important considerations when selecting the optimal approach for practical applications. Therefore, rational design of synthesis strategies (guided by the interplay of polymer type, energy-level alignment, morphology, surface area, and porosity) is essential for achieving high-performance polymer-semiconductor photocatalysts.

4.10. Light absorption

Efficient light absorption is a fundamental prerequisite for high photocatalytic activity because it determines the number of photogenerated electrons and holes available for surface reactions. Semiconductors like TiO2 or ZnO are limited by their wide band gaps, which absorb primarily ultraviolet light and leave most of the visible spectrum untapped. The incorporation of organic polymers into semiconductor composites provides a versatile strategy to extend light absorption into the visible range. Conjugated and conducting polymers possess tunable HOMO–LUMO gaps and strong π–π conjugation, which enable the efficient capture of visible photons and sensitization of the semiconductor.138–141

Polymer incorporation not only broadens the spectral response but also allows for the selective tuning of absorption edges through molecular design, functional group modification, or co-polymerization.142–144 Compared with conventional doping or inorganic sensitization, polymer-based approaches show greater flexibility and milder synthesis conditions. Additionally, polymer-semiconductor composites with hierarchical morphology and porous structures (as discussed in Sections 4.4–4.6) enhance light harvesting through scattering and multiple reflections, which effectively increase the optical path length. Therefore, the combination of polymer sensitization and controlled structural design leads to superior light absorption compared with pristine semiconductors.125

Excessive polymer coverage or aggregation can create shading effects that limit light penetration to the semiconductor and reduce overall photocatalytic efficiency. This highlights the need for optimal polymer loading and uniform distribution, which can be achieved through controlled synthesis strategies like in situ polymerization or self-assembly (Subsection 4.9). The ability to engineer light absorption through polymer incorporation and morphological optimization is a key advantage of polymer-semiconductor composites over conventional photocatalysts.

4.11. Charge recombination suppression

Suppressing electron–hole recombination is equally critical for achieving high photocatalytic efficiency. In pure semiconductors, photogenerated charges recombine rapidly, which limits quantum efficiency. Organic polymer incorporation provides multiple mechanisms to mitigate this limitation. First, polymers can serve as electron or hole acceptors that facilitate directional charge transfer and spatial separation of carriers. This interfacial charge extraction reduces the likelihood of recombination and prolongs carrier lifetimes.145–147

The effectiveness of recombination suppression depends strongly on the type of polymer, interfacial interaction, and energy-level alignment. Covalently bonded or strongly coordinated polymer-semiconductor interfaces generally provide faster charge transfer pathways and more efficient recombination suppression compared with physically adsorbed systems. Additionally, conducting polymers with high carrier mobility further enhance charge separation efficiency, while non-conjugated or insulating polymers provide minimal recombination mitigation despite improving surface adsorption or dispersion.128,148,149

Morphology and porosity also influence recombination dynamics. Nanostructured, hierarchical, and porous composites reduce the distance that photogenerated charges must travel to reach reactive sites, which minimizes bulk recombination.141,150,151 Conversely, dense or poorly connected structures increase carrier diffusion distances, which promote recombination even in the presence of polymers. Therefore, charge recombination suppression is an integrated outcome of polymer chemistry, interfacial engineering, and structural design.

The dual optimization of light absorption and charge recombination suppression is fundamental to maximizing the photocatalytic performance of polymer-semiconductor composites. Effective light harvesting generates abundant charge carriers, while strong interfacial coupling and optimized morphology ensure that these carriers are efficiently separated and utilized in surface redox reactions, which provide a clear advantage over pure semiconductor photocatalysts.

4.12. Stability

Chemical and structural stability is a critical requirement for practical photocatalysts because it ensures consistent performance under operational conditions. Pure inorganic semiconductors (particularly narrow-band-gap materials like CdS or Cu2O) are prone to photocorrosion, leaching, or surface degradation when exposed to light, moisture, or reactive species. Organic polymer-semiconductor composites enhance stability by providing protective polymer layers that shield the semiconductor from direct contact with harsh environments. Polymers also act as structural support, preventing particle aggregation and maintaining dispersion, which preserves active site accessibility over time.

The effectiveness of stability enhancement is strongly influenced by polymer type, interfacial interactions, morphologies, and synthesis methods. Conjugated and conducting polymers with rigid backbones present greater chemical resistance than non-conjugated or flexible polymers.152–154 Composites prepared through in situ polymerization or covalent grafting exhibit superior stability compared with physically mixed systems due to stronger interfacial adhesion, which minimizes the detachment or leaching of the polymer and semiconductor components. Additionally, hierarchical or core–shell morphologies further protect the semiconductor by introducing multiple barriers against photochemical or chemical attack.

Excessive polymer loading or poorly designed interfaces can inadvertently show stability by blocking reactive sites or inducing mechanical stress. Therefore, an optimized balance between polymer coverage and semiconductor exposure is essential to maximize both stability and photocatalytic activity. Compared with bare semiconductors, well-engineered polymer-semiconductor composites consistently demonstrate improved chemical robustness and prolonged operational lifetimes, making stability a key factor in activity tuning for practical applications.

4.13. Photo-durability

Photo-durability refers to the ability of a photocatalyst to resist degradation under continuous light irradiation, which is crucial for sustaining long-term photocatalytic performance. Pure semiconductors are susceptible to photochemical corrosion or oxidative damage due to the accumulation of photogenerated charges on their surfaces. Organic polymer-semiconductor composites enhance photo-durability by facilitating efficient charge separation and extraction and hence reduce the localized charge buildup that initiates photo-corrosion.

The type of polymer and the quality of the polymer-semiconductor interface are critical for photo-durability. Conducting and conjugated polymers with robust backbones act as efficient electron or hole acceptors that transport carriers away from the semiconductor and minimize recombination-induced damage.110,117 Strong interfacial interactions like covalent bonding or coordination further stabilize the composite and prevent polymer leaching or surface deterioration under prolonged irradiation.155 In contrast, weakly adsorbed polymers or poorly aligned interfaces provide limited protection, which results in faster photodegradation.

Morphology also plays a significant role. Hierarchical, core–shell, or porous structures distribute photogenerated charges more evenly and reduce local hot spots, which mitigate photo-corrosion. Therefore, polymer-semiconductor composites with optimized morphology and interfacial design show superior photo-durability compared with bare semiconductors or simple physically mixed systems. This improvement allows the composites to maintain high photocatalytic activity over extended reaction times, which highlights the importance of photo-durability as a key factor in long-term activity tuning for practical applications.

4.14. Recyclability

Recyclability is a crucial performance metric for practical photocatalysts, which reflects their ability to maintain activity over multiple reaction cycles without a significant loss of efficiency. Pure inorganic photocatalysts suffer from aggregation, leaching, or surface fouling during repeated use, which reduces the number of accessible active sites and compromises long-term performance. The incorporation of organic polymers into semiconductor composites mitigates these issues by enhancing structural integrity, dispersibility, and interfacial robustness.

Polymers act as stabilizing matrices that prevent nanoparticle agglomeration and maintain uniform exposure of active sites throughout successive cycles. Strong interfacial interactions ensure that both the polymer and semiconductor components remain intact, which preserves the composite architecture. Conducting or conjugated polymers further facilitate charge extraction during each cycle and prevent the accumulation of charges that can degrade the catalyst over time.126,156,157 Compared with physically blended systems or bare semiconductors, polymer-semiconductor composites typically retain a higher fraction of initial activity after multiple runs and show superior practical applicability.

Sajith et al.50 investigated the photocatalytic activity of PAn-TiO2 composites after several recycling processes. The photocatalytic performance of TiO2 decreases rapidly compared to PAn-TiO2 composites during recycling, as illustrated in Table 3. During recycling, the organic polymer stabilizes the TiO2 and makes the composites easy to recycle.

Table 3. Photocatalytic performance comparison between pure TiO2 and PAn-TiO2 composites during recycling.

No. of cycles Percentage degradation by TiO2 (%) Percentage degradation by PAn-TiO2 (%)
1 68 96
2 29 90
3 20 85

However, recyclability is influenced not only by mechanical stability but also by chemical resilience. Polymers prone to photodegradation, hydrolysis, or oxidative attack can compromise composite performance over repeated cycles. Therefore, careful selection of robust polymer backbones, controlled polymer loading, and optimized synthesis strategies are essential to achieve consistent recyclability. When these design principles are implemented, polymer-semiconductor composites provide a reliable and reusable photocatalyst platform that combines high activity with long-term operational stability. This is a significant advantage over bare photocatalysts.

A summary of the different photocatalytic tuning factors is presented in Table 4, which indicates the performance efficiency of the photocatalytic composites.

Table 4. Factors governing the photocatalytic performance of organic polymer-semiconductor composites.

Tuning factor Role in photocatalysis Advantages Controlling Impact on photocatalytic activity Challenges
Type of polymer Determine the light absorption, conductivity, and charge extraction ability Tailorable properties, enable visible-light activity Electronic and physicochemical properties Strongly influences activity level and reaction scope Trade-off between activity and stability
Chemical structure of polymers Controls adsorption, interfacial bonding, and charge delocalization Fine-tuning at the molecular level possible Conjugation length, functional groups, donor–acceptor units Enhances selectivity, charge separation, and kinetics Complex synthesis, structure–property trade-offs
Band gap engineering Extends absorption into the visible/solar region Improves solar efficiency Light absorption range Increases photon utilization and carrier generation Narrow band gaps can increase recombination
Energy-level alignment Governs the thermodynamic feasibility of electron/hole transfer Enables Z-/S-scheme operation Direction of charge flow Determines the efficiency of charge separation and redox strength Requires precise electronic matching
Interfacial charge transfer mechanisms Controls recombination against the utilization of carriers Balances separation and redox power Carrier separation pathway Z-/S-scheme > type-II > type-I in performance Interface engineering complexity
Morphology Impacts charge migration distance and light scattering Hierarchical structures boost efficiency Structural architecture Improve kinetics and carrier transport Overcomplexity can reduce stability
Surface area Enhances adsorption and surface reactions Improves pollutant degradation efficiency Number of active sites Increases reaction rates Excess polymer can block active sites
Porosity Facilitates reactant/product diffusion and light trapping Improves accessibility and utilization Mass transport and diffusion Enhances practical catalytic efficiency Poorly controlled porosity weakens the structure
Composite synthesis strategies Determines interfacial contact and defect density Enables tailored interfaces Interface quality and dispersion Directly impacts charge transfer efficiency Scalability and reproducibility issues
Light absorption Governs the initial excitation process Essential for solar-driven catalysis Photon harvesting efficiency Higher absorption leads to higher activity Excess absorption can cause heat loss
Charge recombination suppression Maintains the availability of electrons and holes Achieved through heterojunctions and polymers Carrier lifetime Major determinant of quantum efficiency Requires optimized interface design
Stability Maintains long-term activity Essential for practical applications Structural and chemical integrity Ensures consistent performance Polymer degradation under irradiation
Photo-durability Prevents activity decay Improves reusability Resistance to photo-oxidation Extends catalyst lifetime Limited for some conjugated polymers
Recyclability Determines economic and environmental viability Important for real-world deployment Catalyst reusability Maintains performance over cycles Polymer leaching or detachment

5. Performance evaluation in environmental and energy applications

The practical utility of organic polymer-semiconductor composites is ultimately measured by their performance in environmental remediation131,158 and energy conversion processes.159 These applications critically depend on the synergistic optimization of light absorption, charge separation, interfacial interactions, morphology, surface area, porosity, and stability, as discussed in Section 4. Composites integrating these factors effectively demonstrate superior photocatalytic activity compared with conventional semiconductors or polymer-free systems.

In environmental applications, polymer-semiconductor composites have been extensively evaluated for the degradation of organic pollutants, like dyes,160 pharmaceuticals,161,162 and other compounds.163–165 Conjugated,166 temperature responsive,21,167 and conducting polymers168 sensitize wide-band-gap semiconductors, which extend light absorption into the visible region and enhance photogenerated carrier production. Porous and hierarchical morphologies facilitate the efficient diffusion of reactants and products, while strong interfacial coupling ensures rapid charge transfer. Comparative studies consistently show that polymer-semiconductor composites outperform bare semiconductors in both reaction rate and pollutant mineralization efficiency, particularly under visible-light irradiation. However, polymer type and loading must be carefully optimized because excessive polymer coverage can reduce active site accessibility and hinder performance.

In energy applications, polymer-semiconductor composites are employed for hydrogen evolution169 and CO2 reduction12 reactions. Here, charge separation and transfer efficiency, light absorption, and photostability are paramount. Conducting polymers, covalently anchored to semiconductors with suitable energy-level alignment, facilitate rapid electron or hole transport, suppress recombination, and preserve strong redox potentials. For hydrogen evolution, composites show significantly higher H2 generation rates than pristine semiconductors, which are attributed to improved light harvesting and enhanced interfacial charge transfer.170 Similarly, in CO2 reduction, polymer-semiconductor composites show increased product selectivity and quantum efficiency due to efficient electron transfer to CO2 molecules at well-designed active sites.171,172

Performance evaluation also highlights the importance of stability, photodurability, and recyclability (Sections 4.12–4.14). High-performing composites retain significant activity over multiple cycles, whereas conventional photocatalysts degrade or lose efficiency due to photocorrosion and aggregation. Hierarchical and porous composites demonstrate faster reaction kinetics and improved mass transport, while polymer-mediated charge separation enhances quantum yields. Comparative studies further emphasize that the interplay among polymer type, morphology, surface area, porosity, and interfacial engineering determines application-specific performance rather than any single factor alone.139,173–176

The superior performance of polymer-semiconductor composites in environmental remediation and energy applications arises from the integration of molecularly tailored polymers, optimized composite architecture, and efficient charge management. Rational design strategies that balance light absorption, charge separation, surface accessibility, and structural stability enable these composites to achieve higher reaction rates, better selectivity, and longer operational lifetimes compared with bare photocatalysts. This performance evaluation underlines the practical relevance of the key activity-tuning factors discussed in Section 4 and guides future optimization efforts for application-specific photocatalysis.

6. Current challenges and limitations

Despite the significant advances and demonstrated advantages of organic polymer-semiconductor composites, several challenges and limitations remain that hinder their widespread application in environmental remediation and energy conversion. A primary challenge lies in achieving optimal interfacial interactions between the polymer and semiconductor. Weak physical adsorption or poorly aligned energy levels can limit charge transfer efficiency, which results in rapid electron–hole recombination and reduced photocatalytic activity, even in composites with high light absorption and surface area. Strong covalent or coordinated interfaces improve performance but often require complex synthesis strategies that can reduce scalability and increase cost.

Another limitation concerns the trade-offs between polymer loading, light absorption, and active site accessibility. Excessive polymer coverage can shield the semiconductor from incident light or block surface reactive sites, which reduces overall efficiency. Conversely, insufficient polymer incorporation can fail to provide adequate sensitization or charge separation benefits. Achieving the optimal balance of polymer type, loading, and distribution remains a persistent challenge, particularly when scaling up from laboratory synthesis to practical applications.

Stability and photo-durability (while generally improved by polymer incorporation) remain a concern under harsh operational conditions. Some polymers are susceptible to photodegradation, oxidation, or hydrolysis over extended use, especially in aqueous or highly oxidative environments. Hierarchical morphologies and porous structures (which enhance light harvesting and mass transport) can also be prone to mechanical collapse or pore blockage over repeated cycles, which limit long-term performance. Therefore, ensuring robust chemical and structural durability while maintaining photocatalytic efficiency is a critical design challenge.

Recyclability and practical implementation present additional limitations. Polymer-semiconductor composites generally demonstrate superior recyclability compared with bare semiconductors, achieving consistent activity over multiple cycles, provided that polymer stability, interfacial bonding, and morphological integrity are carefully maintained. Moreover, most studies to date have focused on small-scale laboratory experiments under controlled conditions, and few studies have addressed large-scale, real-world applications involving complex pollutant mixtures or variable solar irradiation.

Synthesis complexity and cost are significant barriers to commercialization. Advanced fabrication techniques such as in situ polymerization, covalent grafting, or template-assisted self-assembly provide excellent control over morphology, porosity, and interfacial interactions but often involve multiple steps, high temperatures, or specialized reagents. Simplifying synthesis without compromising composite performance remains a key limitation for practical deployment.

Organic polymer-semiconductor composites show superior light absorption, charge separation, and structural tunability compared with conventional photocatalysts, while challenges related to interfacial optimization, polymer loading, stability, recyclability, and scalable synthesis continue to limit their widespread adoption. Addressing these limitations is essential for translating laboratory successes into practical environmental and energy applications and guides future research directions discussed in the next section.

7. Future perspectives and research directions

Several scientific and technological challenges continue to limit their practical implementation even after the remarkable progress achieved in organic polymer-semiconductor photocatalysts. Future research should move beyond simply improving photocatalytic activity and focus on developing next-generation systems that show high efficiency, scalability, long-term stability, sustainability, and mechanistic understanding. In this regard, the future of polymer-semiconductor photocatalysis will likely be driven by advances in molecular engineering, interfacial design, artificial intelligence-assisted material discovery, operando characterization techniques, and integrated solar-energy conversion technologies.

One of the most important future directions is the rational molecular design of polymers with precisely tailored electronic structures. Most current studies rely on commercially available polymers or relatively simple polymer architectures. Nevertheless, the electronic properties of polymers can be systematically tuned through the control of conjugation length, side-chain engineering, heteroatom incorporation, donor–acceptor composition, and functional group modification. Future polymer design should focus on achieving simultaneous optimization of visible-light absorption, charge mobility, interfacial compatibility, and photostability. Donor–acceptor conjugated polymers with controllable HOMO–LUMO levels are expected to play a central role in constructing highly efficient photocatalytic systems. Such materials could provide unprecedented control over charge transfer pathways and energy-level alignment, which enable photocatalysts specifically tailored for targeted reactions such as CO2 reduction, hydrogen evolution, or selective organic synthesis.

Another suitable research direction involves the development of advanced S-scheme heterojunctions. Recent studies have demonstrated that S-scheme systems outperform many conventional type-II and Z-scheme photocatalysts because they simultaneously maintain efficient charge separation and strong redox capability. However, the design principles governing S-scheme formation in polymer-semiconductor composites remain incompletely understood. Future investigations should focus on establishing quantitative relationships between Fermi-level differences, band bending, interfacial electric fields, and photocatalytic performance. Advanced polymer architectures capable of generating strong built-in electric fields can provide a powerful platform for constructing highly efficient S-scheme photocatalysts. Therefore, the integration of conjugated polymers, polymeric semiconductors, and conducting polymers into S-scheme systems is expected to become one of the most active research areas in the coming decade.

The emergence of covalent organic frameworks (COFs), conjugated microporous polymers (CMPs), porous organic polymers (POPs), and other crystalline polymeric semiconductors represents another transformative opportunity. Compared with conventional polymers, these materials show highly ordered structures, large surface areas, tunable porosity, and controllable electronic properties. Their well-defined architectures facilitate efficient charge transport and provide excellent platforms for constructing heterojunction photocatalysts. Future research should focus on integrating these advanced polymeric semiconductors with inorganic semiconductors to create multifunctional systems capable of maximizing light harvesting, charge separation, and catalytic activity simultaneously.

New research should also be directed toward stimuli-responsive and adaptive photocatalytic systems. Most existing photocatalysts operate as static materials whose properties remain unchanged during reactions. In contrast, next-generation photocatalysts should possess the ability to dynamically respond to environmental changes such as temperature, pH, light intensity, pollutant concentration, or reaction intermediates. Stimuli-responsive polymers can alter their charge-transport behavior, surface chemistry, and adsorption characteristics in response to external stimuli, which enables self-regulating photocatalytic systems. Such adaptive materials can improve selectivity, catalytic efficiency, and durability under real-world operating conditions, particularly in complex wastewater treatment and solar fuel production applications.

Future research should also prioritize precise interfacial engineering at the molecular and atomic levels. The interface between polymers and semiconductors largely determines charge separation efficiency, carrier migration pathways, and overall photocatalytic activity. Nonetheless, many current studies still rely on empirical synthesis approaches without fully understanding the underlying interfacial interactions. Advanced interface construction strategies involving covalent coupling, single-atom catalysts, molecular bridges, and engineered surface functionalization should be explored to establish stronger electronic communication between polymer and semiconductor components. Such approaches could significantly reduce charge-transfer resistance and further suppress electron–hole recombination.

Another critical challenge is the limited understanding of real-time photocatalytic processes. Most mechanistic interpretations are currently based on indirect experimental evidence. Future investigations should increasingly employ operando and in situ characterization techniques like in situ X-ray photoelectron spectroscopy, synchrotron-based analyses, Kelvin probe force microscopy, transient absorption spectroscopy, electron paramagnetic resonance spectroscopy, and ultrafast spectroscopic methods. These techniques can directly monitor charge transfer, surface reactions, intermediate formation, and catalyst evolution during photocatalysis. Such insights will enable researchers to establish more reliable structure–property–performance relationships and rationally design next-generation photocatalysts.

The integration of artificial intelligence (AI), machine learning (ML), and high-throughput computational screening is expected to revolutionize photocatalyst discovery. Traditional trial-and-error approaches are time-consuming and inefficient due to the enormous number of possible polymer structures and semiconductor combinations. AI-driven approaches can rapidly predict electronic structures, adsorption properties, energy-level alignments, and photocatalytic performance, which significantly accelerate material discovery. In combination with density functional theory (DFT) calculations and experimental validation, machine learning may enable the development of predictive frameworks for designing highly efficient polymer-semiconductor photocatalysts.

Future research should move beyond model pollutants and laboratory-scale demonstrations toward real-world photocatalytic systems. Many photocatalysts exhibit excellent performance under controlled laboratory conditions but fail when applied to actual wastewater, industrial effluents, or outdoor solar irradiation. Therefore, future studies should evaluate photocatalysts under realistic operating conditions, like complex pollutant mixtures, varying environmental parameters, and long-term operation. Additionally, reactor design, catalyst immobilization, and scale-up strategies should receive greater attention to bridge the gap between laboratory research and industrial implementation.

Another rapidly growing area is photocatalytic CO2 conversion and solar fuel production. Although pollutant degradation remains the dominant application of polymer-semiconductor composites, future research is expected to focus increasingly on converting solar energy into chemical fuels. Advanced polymer-semiconductor heterojunctions with optimized charge-transfer pathways could enable highly selective reduction of CO2 into valuable products like methanol, methane, formic acid, and syngas. Similarly, photocatalytic hydrogen evolution and overall water splitting are likely to remain major research priorities due to their potential role in future renewable energy systems.

Sustainability considerations should also become a central component of future photocatalytic research. The development of environmentally benign materials, recyclable photocatalysts, green synthesis methods, and bio-based polymers will be essential for achieving large-scale deployment. Biological polymer-semiconductor composites derived from chitosan, cellulose, lignin, and other renewable resources can provide environmentally friendly alternatives to synthetic polymers. Future studies should focus on enhancing the electronic functionality of these materials while preserving their sustainability advantages.

The next generation of photocatalytic systems will likely evolve toward multifunctional and integrated platforms that simultaneously combine light harvesting, pollutant degradation, sensing, energy conversion, and environmental monitoring. Rather than optimizing a single performance parameter, future research should aim to develop intelligent photocatalytic systems capable of addressing multiple environmental and energy challenges simultaneously. Such multifunctional materials could play a key role in the transition toward sustainable technologies and circular energy economies.

The future of organic polymer-semiconductor photocatalysis lies in the convergence of advanced polymer chemistry, S-scheme heterojunction design, interfacial engineering, operando characterization, artificial intelligence-assisted materials discovery, and sustainable manufacturing. Progress in these areas will not only enhance photocatalytic efficiency but also facilitate the development of robust, scalable, and commercially viable photocatalytic technologies for environmental remediation, solar fuel production, and broader energy applications. This transition from activity optimization to intelligent photocatalyst design represents the next major frontier in polymer-semiconductor photocatalysis research.

8. Conclusion

Organic polymer-semiconductor composites represent a versatile and highly tunable class of photocatalysts with significant potential for environmental remediation and energy conversion applications. This review highlighted how the interplay among polymer chemistry, energy-level alignment, interfacial charge transfer, morphology, stimuli responsiveness, surface area, porosity, and stability controls photocatalytic performance. These composites show enhanced light absorption, improved charge separation, and extended spectral response, which results in higher reaction rates, better selectivity, and longer operational lifetimes, compared with pure semiconductors.

Critical factors like polymer type, band gap engineering, interfacial mechanisms, and composite architecture have been identified as key activity-tuning parameters, while synthesis strategies (in situ polymerization, covalent grafting, and self-assembly) enable precise control over structure and performance. Performance evaluations demonstrate the superiority of polymer-semiconductor composites in pollutant degradation, hydrogen evolution, and CO2 reduction, indicating that challenges related to stability, photodurability, recyclability, and scalable fabrication have been addressed.

Future research should focus on rational polymer design, robust interfacial engineering, hierarchical morphologies, and scalable synthesis approaches to further enhance light harvesting, charge separation, and durability. Integration with co-catalysts, advanced heterojunctions, and computational design tools will accelerate the development of high-performance, application-ready composites. Polymer-semiconductor composites provide a suitable pathway for sustainable photocatalysis, and continued interdisciplinary efforts will be essential to translate laboratory innovations into practical environmental and energy solutions.

Organic polymer-semiconductor composites represent a powerful and adaptable platform for photocatalytic applications. By tuning the polymer structure, interfacial interactions, and composite architecture, photocatalytic activity can be significantly enhanced. This review highlights the main factors governing performance and provides a mechanistic framework for future material design. Continued interdisciplinary efforts combining chemistry, materials science, and engineering will accelerate the development of efficient, stable, and sustainable photocatalytic systems.

Conflicts of interest

There are no conflicts of interest.

Abbreviations

PPy

Polypyrrole

AM

Azithromycin

CM

Carmoisine

NPs

Nanoparticles

ROS

Reactive oxygen species

CB

Conduction band

VB

Valence band

NDZ

Nb-doped ZnO

PVAc

Polyvinyl acetate

BPA

Bisphenol A

BTB

Bromothymol blue

PTh

Polythiophene

RhB

Rhodamine-B

PAn

Polyaniline

HOMO

Highest occupied molecular orbital

LUMO

Lowest unoccupied molecular orbital

PVA

Polyvinyl alcohol

PEG

Polyethylene glycol

PMMA

Poly(methyl methacrylate)

PAA

Polyacrylic acid

PEDOT

Poly(3,4-ethylenedioxythiophene)

COF

Covalent organic frameworks

CMP

Conjugated microporous polymers

PNIPAM

Poly(N-isopropylacrylamide)

PNIPMAM

Poly(N-isopropylmethacrylamide)

E g

Bandgap energy

CS

Chitosan

RGO

Reduced graphene oxide

GO

Graphene oxide

Acknowledgments

Muhammad Arif is thankful to the University of Management and Technology, Lahore-54770, Pakistan.

Biography

Muhammad Arif.

Muhammad Arif

Dr Muhammad Arif is serving as a Professor (Assistant) of Chemistry in the Department of Chemistry, University of Management and Technology, Lahore, since 2022. He has been working as a Lecturer in Chemistry at the Department of Chemistry, School of Science, University of Management and Technology, Lahore, from 2017 to 2022. He obtained his PhD in Chemistry from the University of the Punjab, Lahore, Pakistan. He obtained his MPhil in Chemistry and MSc in Organic Chemistry from Quaid-i-Azam University Islamabad, Islamabad, and the Institute of Chemistry, University of the Punjab, Lahore, Pakistan, respectively. His research interests include the synthesis, characterization and applications of metal nanoparticles fabricated in microgels, ligands, and semiconductors.

Data availability

No primary research results, software or codes have been included and no new data were generated or analysed as part of this review.

References

  1. Valdovinos-Flores C. Industrialization and its environmental impact on health and pollution in the Santiago River Basin of Mexico. Int. J. Environ. Sci. Technol. 2025;22(15):16247–16260. doi: 10.1007/s13762-025-06708-7. [DOI] [Google Scholar]
  2. ul Hassan M. Siddique H. M. A. Alvi S. Impacts of industrialization, trade openness, renewable energy consumption, and urbanization on the environment in South Asia. Environ. Dev. Sustain. 2025;27(11):28087–28110. doi: 10.1007/s10668-024-05846-1. [DOI] [Google Scholar]
  3. Preonty N. E. J. Hassan M. N. Reza A. H. M. S. Rasel M. I. A. Mahim M. M. A. Jannat M. F. T. Pollution and health risk assessment of heavy metals in surface water of the industrial region in Gazipur, Bangladesh. Environ. Chem. Ecotoxicol. 2025;7:527–538. doi: 10.1016/j.enceco.2025.02.014. [DOI] [Google Scholar]
  4. Omokpariola D. O. Omokpariola P. L. Okechukwu V. U. Okeke A. P. Daramola A. A. Assessing the role of Persistent Organic Pollutants (POPs) in cancer development in Nigeria: environmental exposure, risk factors, and policy gaps. Discovery Toxicol. 2025;2(1):9. doi: 10.1007/s44339-025-00030-0. [DOI] [Google Scholar]
  5. Saini R. and Choudhary K., Toxic potential of azo dyes: A broader understanding, in Hazardous Chemicals: Overview, Toxicological Profile, Challenges, and Future Perspectives, 2025, pp. 469–481, 10.1016/B978-0-323-95235-4.00039-6 [DOI] [Google Scholar]
  6. Qi X. Zhao R. Zhang X. Ru S. Xiong J. Q. Multiomics unraveled that gibberellin signaling underlies adaptation of rice to ciprofloxacin stress: Calling for concerns on the adverse effects of pharmaceutical residues in water during agricultural irrigations. J. Hazard. Mater. 2025;485:136818. doi: 10.1016/j.jhazmat.2024.136818. [DOI] [PubMed] [Google Scholar]
  7. Hamrouni D. Hasni R. Ben Jebli M. The Impact of Economic Complexity in Trade, Technology, and Research on CO2 Emissions: Evidence from OECD Countries. Environ. Chem. Ecotoxicol. 2025;30(3):487–504. doi: 10.1007/s10666-025-10021-5. [DOI] [Google Scholar]
  8. Derkaoui K. Bencherifa I. Elfiad A. Mebdoua Y. Belkhettab I. Boukhouidem K. Benredouane S. Hadjersi T. Manseri A. Kechouane M. Unveiling the Optical and Dielectric Properties of MnFe2O4: A High-Performance Visible-Light Photocatalyst for Sustainable Rhodamine B Degradation. J. Electron. Mater. 2025;54(7):5271–5286. doi: 10.1007/s11664-025-11991-8. [DOI] [Google Scholar]
  9. Wang J. Niu X. Wang R. Zhang K. Shi X. Yang H. Y. Ye J. Wu Y. High-entropy alloy-enhanced ZnCdS nanostructure photocatalysts for hydrogen production. Appl. Catal. B Environ. Energy. 2025;362:124763. doi: 10.1016/j.apcatb.2024.124763. [DOI] [Google Scholar]
  10. Lakshmi G. Velusamy P. Porous β-CD polymer-based metal oxide systems: in-situ construction and tuning for boosted photocatalytic performance. J. Inclusion Phenom. Macrocyclic Chem. 2026:1–15. doi: 10.1007/s10847-025-01326-9. [DOI] [Google Scholar]
  11. Nagatsuka K. Yoshino S. Yamaguchi Y. Kudo A. Facile Z-Scheme Photocatalyst Sheets Consisting of Metal Sulfides and Poly-3,4-ethylenedioxythiophene of a Conductive Polymer for Visible-Light-Driven Water Splitting. Energy Fuel. 2025;39:17021–17028. doi: 10.1021/acs.energyfuels.5c02135. [DOI] [Google Scholar]
  12. Su K. Yuan S. X. Feng Y. X. Dong G. X. Mu Y. F. Zhang M. Lu T. B. Polymer-assisted in-situ growth of Cs3Sb2Br9 on Co3O4 to boost sacrificial-agent-free photocatalytic CO2 reduction. Rare Met. 2025;44(5):3194–3205. doi: 10.1007/s12598-024-02968-3. [DOI] [Google Scholar]
  13. Kolahdouzan F. Goodarzi N. Setayeshmehr M. Mousavi D. S. Moshfegh A. Z. 1D-based nanostructures in photocatalytic CO2 reduction. Chin. J. Catal. 2025;70:230–259. doi: 10.1016/S1872-2067(24)60214-7. [DOI] [Google Scholar]
  14. Shrivastav H. Kaur H. Kumar S. Sur D. Sadaf S. Kaur R. Kumar C. Patial P. Awad M. Alam M. W. A new horizon in green synthesis for metal oxides: Dracaena reflexa-derived TiO2 nanoparticles for photocatalytic activity and antibacterial application. Catal. Today. 2026;466:115679. doi: 10.1016/j.cattod.2026.115679. [DOI] [Google Scholar]
  15. Rangappa A. P. Kumar D. P. Do K. H. Gopannagari M. Reddy K. A. J. Ruan X. Ravi S. K. Zhao J. Zhang Y. Kim T. K. Self-confined oxidation domains in dual-metal sulfide catalyst enables active sites for selective photoconversion of carbon dioxide to methanol by pure water. Mater. Sci. Eng. R Rep. 2026;167:101093. doi: 10.1016/j.mser.2025.101093. [DOI] [Google Scholar]
  16. Mei Y.-C. Geleta T. A. Miri A. Venkatesan P. Chao Y.-C. Chen Y. Chou P.-H. Tee R. Q. Shih Y. One-step synthesis of porous chlorine-modified graphitic carbon nitrides for efficient photocatalytic degradation of bisphenol A: DFT insights and mechanistic pathways under visible light. J. Environ. Chem. Eng. 2026;14:121018. doi: 10.1016/j.jece.2025.121018. [DOI] [Google Scholar]
  17. Gunasekaran E. Saravanan E. Jayakumar V. S. Govindarajan S. Bio-Engineered Chitosan–ZnO–ZnFe2O4 Heterojunction with Tunable Bandgap and Boosted Charge Dynamics for UV-Driven Photocatalytic Mineralization. ChemistrySelect. 2026;11:e03654. doi: 10.1002/slct.202503654. [DOI] [Google Scholar]
  18. Trabelsi A. B. G. Alkallas F. H. Rabia M. Conversion of Seawater to H2 Fuel Using a Promising Photocathode Based on Bismuth(III) Oxide Iodide–Poly(2-Aminobenzene-1-Thiol) With Intercalated Iodide as a Multilayer Spherical Nanocomposite. Int. J. Energy Res. 2026:6987666. doi: 10.1155/er/6987666. [DOI] [Google Scholar]
  19. Aroob S. Taj M. B. Maria A. Bibi I. Khan M. I. Beagan A. M. Synergistic effects of the pyrite and graphitic carbon nitride-based bio-polymer composite for enhancing the photocatalytic degradation of reactive red-24 dye. New J. Chem. 2025;49:16271–16287. doi: 10.1039/D5NJ02732B. https://dx.doi.org/10.1039/d5nj02732b [DOI] [Google Scholar]
  20. Tan Z. Song T. Liu Y. Sun H. Dai Y. Yu J. Poly (ionic liquid-co-acrylic acid)/oxidized carbon nitride (P/P/O) with enhanced photocatalytic and synergistic bacteriostasis performance. J. Photochem. Photobiol., A. 2025;466:116367. doi: 10.1016/j.jphotochem.2025.116367. [DOI] [Google Scholar]
  21. Vadivellu K. Osman E. Chandren S. Bahru J. Hollow Silica-Encapsulated TiO2 Functionalized with pH-Responsive Poly(acrylic acid) for Photocatalytic Degradation of Bisphenol A. J. Mater. Life Sci. 2025;4:90–101. doi: 10.11113/jomalisc.V4.108. [DOI] [Google Scholar]
  22. Yang X. Luo H. Chen S. Peng J. He G. Guo R. Zhang D. Boosted high-temperature capacitive energy storage in D-A-D type semiconductor/polymer composite via constructing physical cross-linking and electronic trapping. Composites, Part A. 2025;196:109019. doi: 10.1016/j.compositesa.2025.109019. [DOI] [Google Scholar]
  23. Podborska A. Górka-Kumik W. Dąbczyński P. Szuwarzyński M. Nanocomposite 1:2 demultiplexer based on surface-grafted poly(methacrylic acid) brushes with in situ-fabricated CdS particles. Eur. Polym. J. 2025;228:113838. doi: 10.1016/j.eurpolymj.2025.113838. [DOI] [Google Scholar]
  24. Mansour A. M. Abou Hammad A. B. El Nahrawy A. M. Exploring nanoarchitectonics and optical properties of PAA-ZnO@BCP wide-band-gap organic semiconductors. Sci. Rep. 2024;14(1):3060. doi: 10.1038/s41598-024-53469-3. [DOI] [PMC free article] [PubMed] [Google Scholar]
  25. Kadhim K. K. Azeez H. M. Tuama Yousif R. Mohammed M. K. Meteab M. H. Boosting the structural, optical and AC electrical characteristics of PVA/CdTe nanocomposites for flexible smart optoelectronic devices. Int. J. Nanoelectron. Mater. 2025;18:527–536. doi: 10.58915/ijneam.v18i4.2617. [DOI] [Google Scholar]
  26. Chen H. C. Lin T. Y. Peng H. C. Lee Y. H. Wang R. C. Versatile g-C3N4/AlOOH nanocomposites: Efficient photocatalyst for dye removal, algae inactivation, and glucose detection. Chemosphere. 2025;371:144033. doi: 10.1016/j.chemosphere.2024.144033. [DOI] [PubMed] [Google Scholar]
  27. Alouche B. Dehbi A. Bassaid S. Yahiaoui A. Alsalme A. Messori M. Polypyrrole–ZnCo2O4 hybrid nanocomposite: synthesis, characterization, and enhanced adsorption-photocatalytic performance for methylene blue degradation. React. Kinet., Mech. Catal. 2025;138(3):1535–1552. doi: 10.1007/s11144-025-02825-z. [DOI] [Google Scholar]
  28. Tang G. Zhang J. Bie C. Zheng X. Jiang C. Yu J. In Situ Soft X-Ray Absorption Spectroscopy Investigation on Charge Transfer Mechanism in COF/CdS S-Scheme Photocatalyst. Adv. Mater. 2025;37:e14576. doi: 10.1002/adma.202514576. https://dx.doi.org/10.1002/ADMA.202514576 [DOI] [PubMed] [Google Scholar]
  29. Yang M. Hao S. Liu L. Li B. Mu Y. Sun J. Chen J. Gao S. Xu Y. Huo L. Synthesis of PANI/NiO porous nanowalls composites for highly NH3 sensing performance at room temperature. Ceram. Int. 2025;51:35644–35653. doi: 10.1016/j.ceramint.2025.05.287. [DOI] [Google Scholar]
  30. Dadsena L. Maharana T. Jujjavarapu S. E. OneWater-driven waste-to-watt innovation: Electroactive Polymer–Metal oxide nanostructures for integrated energy production and reuse of wastewater. Environ. Res. 2026;293:123764. doi: 10.1016/j.envres.2026.123764. [DOI] [PubMed] [Google Scholar]
  31. Trabelsi A. B. G. Alkallas F. H. Rabia M. Infrared-responsive spherical molybdenum oxide/Cl–Poly(N-methylpyrrole) photocathode for sustainable hydrogen generation from seawater. J. Mater. Sci.: Mater. Electron. 2026;37(3):205. doi: 10.1007/s10854-025-16439-7. [DOI] [Google Scholar]
  32. Eswaran A. Subramaniam R. Thirumalainambi M. Annadurai G. Shankar V. Effective photocatalysis and toxicity investigations in zebra fish embryos using highly selective hydrogen sensors and supercapacitor electrode materials for SnO 2 –PANI nanocomposites. Nanoscale Adv. 2026;8(7):2378–2397. doi: 10.1039/D5NA00783F. https://dx.doi.org/10.1039/d5na00783f [DOI] [PMC free article] [PubMed] [Google Scholar]
  33. Jiang R. Lu G. Zhang L. Chen Y. Liu J. Yan Z. Xie H. Insight into the effect of microplastics on photocatalytic degradation tetracycline by a dissolvable semiconductor-organic framework. J. Hazard. Mater. 2024;463:132887. doi: 10.1016/j.jhazmat.2023.132887. [DOI] [PubMed] [Google Scholar]
  34. Tanuj Anjali Kumar R. Kumar S. Rawat D. S. Sustainable fabrication of PVAc-coated Nb–ZnO nanocomposites using Aegle marmelos L. extract for enhanced surface activity towards photocatalytic degradation of bisphenol A and bromothymol blue. Dalton Trans. 2026;55:3475–3499. doi: 10.1039/D5DT02960K. https://dx.doi.org/10.1039/d5dt02960k [DOI] [PubMed] [Google Scholar]
  35. Sawut A. Wu T. Simayi R. Wu T. Gong X. Wang Z. Reduced graphene oxide-TiO2/sodium alginate/polyacrylamide composite hydrogel for enhanced adsorption-photocatalytic degradation of methylene blue. Colloids Surf., A. 2023;678:132531. doi: 10.1016/j.colsurfa.2023.132531. https://dx.doi.org/10.1016/J.COLSURFA.2023.132531 [DOI] [Google Scholar]
  36. Akhtar M. Shahzadi S. Arshad M. Akhtar T. Saeed Ashraf Janjua M. R. Metal oxide-polymer hybrid composites: a comprehensive review on synthesis and multifunctional applications. RSC Adv. 2025;15:18173–18208. doi: 10.1039/D5RA01821H. https://dx.doi.org/10.1039/d5ra01821h [DOI] [PMC free article] [PubMed] [Google Scholar]
  37. Losetty V. Lakkaboyana S. K. Chappidi H. Y. Venkateswarlu K. Trilaksana H. Koduru J. R. Yuzir A. Atanase L. I. Seepana P. K. Knani S. Transformative Applications of Polymer-Based Metal Oxide Nanocomposites in Medicine, Industry, and Environmental Remediation: A Review. J. Inorg. Organomet. Polym. Mater. 2025;36(1):64–96. doi: 10.1007/s10904-025-03707-6. [DOI] [Google Scholar]
  38. Liu S. Zhou L. Zhong T. Wu X. Neyts K. Sulfide/Polymer Composite Solid-State Electrolytes for All-Solid-State Lithium Batteries. Adv. Energy Mater. 2024;14:2403602. doi: 10.1002/aenm.202403602. [DOI] [Google Scholar]
  39. Arif M. Photocatalytic degradation of dyes by metal sulfide–chitosan based composites: a comprehensive review. RSC Adv. 2026;16:5353–5373. doi: 10.1039/D5RA07777J. https://dx.doi.org/10.1039/d5ra07777j [DOI] [PMC free article] [PubMed] [Google Scholar]
  40. Arif M. Tunable photocatalytic activity of metal oxides: designing, principles, parameters, and progress. J. Environ. Manage. 2025;395:127697. doi: 10.1016/j.jenvman.2025.127697. https://dx.doi.org/10.1016/J.JENVMAN.2025.127697 [DOI] [PubMed] [Google Scholar]
  41. Tan H. Zhong H. Deng L. Zhou J. Xu A. Wu D. Chen S. Significantly improved energy storage performance of polyetherimide-based dielectric composites via employing core-shell organic-semiconductor@BaTiO3 nanoparticles. J. Power Sources. 2025;628:235888. doi: 10.1016/j.jpowsour.2024.235888. [DOI] [Google Scholar]
  42. Dang Khoa T. Hoang Duc L. T. Nghi P. D. Huynh H. T. T. Hieu N. T. N. Minh D. T. C. Nam N. T. H. Thao N. T. D. Hoang P. L. K. Hieu N. H. Synthesis of tin selenide nanoparticles using Polygonum avicular extract decorated on graphitic carbon nitride for enhancing photodegradation of amoxicillin trihydrate and photoproduction of hydrogen peroxide. Mater. Chem. Phys. 2025;329:130032. doi: 10.1016/j.matchemphys.2024.130032. [DOI] [Google Scholar]
  43. Jadoun S. Jangid N. K. Fuentes J. P. Yáñez J. Solar-Assisted Synthesis of Poly(o-phenylenediamine)@Zinc Oxide Composites for Photocatalytic Cu(II) Ion Removal. ACS Appl. Polym. Mater. 2025;7:10741–10753. doi: 10.1021/acsapm.5c01958. https://dx.doi.org/10.1021/ACSAPM.5C01958 [DOI] [Google Scholar]
  44. Li X. Zhang L. Jia W. Ma C. Jia X. Liu B. Chen Y. Wang X. Nanoconstructing ZnWO4/sulfur-doped polyimide Z-scheme heterojunction with improved charges transfer for enhanced solar photocatalysis. Sol. Energy. 2025;301:113981. doi: 10.1016/j.solener.2025.113981. https://dx.doi.org/10.1016/J.SOLENER.2025.113981 [DOI] [Google Scholar]
  45. Zhang Y. Li X. Xu W. Cheng Y. Dong S. Li N. Xu Q. Li H. Chen D. Lu J. Toluene-induced framework expansion in carbazole-based porous organic polymers anchored with Cu-ZnIn2S4 for ultrafast azeotropic wastewater recovery. Chem. Eng. J. 2025;512:162369. doi: 10.1016/j.cej.2025.162369. https://dx.doi.org/10.1016/J.CEJ.2025.162369 [DOI] [Google Scholar]
  46. Sun J. Liu H. Wang S. Zhang Y. Bie C. Zhang L. In situ irradiated XPS investigation on S-scheme ZnIn2S4@COF-5 photocatalyst for enhanced photocatalytic degradation of RhB. J. Materiomics. 2025;11:100975. doi: 10.1016/j.jmat.2024.100975. https://dx.doi.org/10.1016/J.JMAT.2024.100975 [DOI] [Google Scholar]
  47. Liu S. Zhang Y. Du J. Xue Y. Huang C. Xu Z. Wang P. Wei Z. Yuan Z. Liao G. Li Q. Facilitating carrier kinetics in dual S-Scheme heterojunctions through interface regulating strategy for H2O2 generation and nizatidine degradation. Chem. Eng. J. 2025;523:168949. doi: 10.1016/j.cej.2025.168949. https://dx.doi.org/10.1016/J.CEJ.2025.168949 [DOI] [Google Scholar]
  48. Hu C. Yin J. Xun S. Zhu L. Li H. He M. Wu P. Li H. Zhu W. Constructing interface chemical coupling S-scheme heterojunction MoO3-x@PPy for enhancing photocatalytic oxidative desulfurization performance: Adjusting LSPR effect via oxygen vacancy engineering. Appl. Catal. B Environ. Energy. 2024;355:124155. doi: 10.1016/j.apcatb.2024.124155. [DOI] [Google Scholar]
  49. Bhankhar A. Sehrawat S. Shukla R. Exploring Structural, Thermal, Optical, and Electrical Dynamics in Polyaniline/Li-Doped NiO Composites for Optimized Charge Transport and Photocatalytic Performance. Polym. Compos. 2026;47:1129–1145. doi: 10.1002/pc.70206. [DOI] [Google Scholar]
  50. Sajith M. Kumari A. H. N. Sambhudevan S. A New Approach for the Photocatalytic degradation of Malachite Green from Aqueous Solution using PANI Modified Metal-Oxide. Water, Air, Soil Pollut.: Focus. 2025;237(3):131. doi: 10.1007/s11270-025-08542-6. [DOI] [Google Scholar]
  51. Yu X. Tian Y. Wei Y. Wang K. Liu Z. Yang F. Chen L. Zhang J. Constructing p–n heterojunctions of Cl-Cu2O and PANI on three-dimensional nanofiber networks for enhanced photocatalytic degradation of oxytetracycline. J. Alloys Compd. 2024;1005:175998. doi: 10.1016/j.jallcom.2024.175998. [DOI] [Google Scholar]
  52. Ponnusamy N. Ravichandran S. Ravichandran S. Saleem S. S. Chinnadurai K. R. Kaium B. Sustainable NiO@Chitosan Hybrid Photocatalysts for Advanced Organic Pollutant Remediation. Part. Part. Syst. Char. 2026;43:e00111. doi: 10.1002/ppsc.202500111. https://dx.doi.org/10.1002/PPSC.202500111 [DOI] [Google Scholar]
  53. Wang Z. Ding G. Li C. Huang H. Xiao Y. Chen Z. Zhang J. Xiao H. Wang Z. Chen L. Shuai L. Ni Y. Liao G. Hydrogen-bonds bridged biomass-assisted S-scheme junction boosts proton-coupled electron transfer for H2O2 photosynthesis. eScience. 2026:100562. doi: 10.1016/j.esci.2026.100562. https://dx.doi.org/10.1016/J.ESCI.2026.100562 [DOI] [Google Scholar]
  54. Hassan F. Qadoos Y. Tanveer A. Saleem A. Younas U. Saeed Z. Ali Z. Ahmad A. Park S. J. Choi D. Nanostructured Ag/CuO-loaded sodium alginate hydrogel beads: A green platform for efficient dye remediation. Mater. Today Commun. 2026;52:115012. doi: 10.1016/j.mtcomm.2026.115012. https://dx.doi.org/10.1016/J.MTCOMM.2026.115012 [DOI] [Google Scholar]
  55. Liu X. Ding G. Guo X. Wang X. Wang Z. Chen Z. Xiao Y. Shuai L. Liao G. Synergizing Donor–Acceptor Ni-MOF with Lignin Proton Relay for Efficient and Selective CO2-to-CO Photoreduction. Adv. Mater. 2025;38:e20384. doi: 10.1002/adma.202520384. https://dx.doi.org/10.1002/ADMA.202520384 [DOI] [PubMed] [Google Scholar]
  56. Chen Z. Ding G. Wang Z. Xiao Y. Liu X. Chen L. Li C. Huang H. Liao G. Precision Molecular Engineering of Carbon Nitride for Efficient and Selective Photoreduction of CO2 to C2H6 in Pure Water. Adv. Funct. Mater. 2025;35:2423213. doi: 10.1002/adfm.202423213. https://dx.doi.org/10.1002/ADFM.202423213 [DOI] [Google Scholar]
  57. Huyen P. T. M. Hung L. T. Tuyet P. T. H. Dan N. H. Ha L. T. V. Quynh T. T. N. Dung N. X. Synthesis and Characterization of ZnO/Chitosan Nanocomposites for Photocatalytic Degradation of Tetracycline in Water Media. Polymers. 2026;18:1114. doi: 10.3390/polym18091114. https://dx.doi.org/10.3390/POLYM18091114 [DOI] [PMC free article] [PubMed] [Google Scholar]
  58. Cerea B. Ribaudo G. Gianoncelli A. Ferroni M. Vassalini I. Alessandri I. Assessing TiO2/Chitosan-Based Hydrogels for Water Remediation: Sunlight-Driven Degradation of Antibiotics in Water. Adv. Mater. Interfaces. 2026:e70544. doi: 10.1002/admi.70544. https://dx.doi.org/10.1002/ADMI.70544 [DOI] [Google Scholar]
  59. Shan T. Li J. Wu S. Wu H. Zhang F. Liao G. Xiao H. Huang L. Chen L. Boosting H2O2 production over carboxymethyl cellulose modified g-C3N4 via hydrogen-bonding-assisted charge transfer. Chem. Eng. J. 2023;478:147509. doi: 10.1016/j.cej.2023.147509. https://dx.doi.org/10.1016/J.CEJ.2023.147509 [DOI] [Google Scholar]
  60. Xiao H. Shan Y. Wu S. Shan T. Luo H. Zhang F. Huang L. Chen L. Liao G. Enlarging the π-conjugation system of carbon nitride for boosting hydrogen peroxide generation. Chem. Eng. J. 2024;492:152228. doi: 10.1016/j.cej.2024.152228. https://dx.doi.org/10.1016/J.CEJ.2024.152228 [DOI] [Google Scholar]
  61. Wang Z. Ding G. Zhang J. Lv X. Wang P. Shuai L. Li C. Ni Y. Liao G. Critical role of hydrogen bonding between microcrystalline cellulose and g-C3N4 enables highly efficient photocatalysis. Chem. Commun. 2023;60:204–207. doi: 10.1039/D3CC04800D. [DOI] [PubMed] [Google Scholar]
  62. Yılmaz Baran N. Yakar A. Türker O. C. Akyol H. K. Baran T. Magnetically recoverable Ag nanoparticles-decorated sodium alginate/TiO2/Fe3O4 hybrid microspheres: Rapid catalytic remediation of toxic organic pollutants and ecotoxicological assessment. Int. J. Biol. Macromol. 2026;362:152116. doi: 10.1016/j.ijbiomac.2026.152116. https://dx.doi.org/10.1016/J.IJBIOMAC.2026.152116 [DOI] [PubMed] [Google Scholar]
  63. Ammouchi N. Zaiter A. Djermoune A. Bouzenad N. Hamrouche N. Abdennouri A. Belhocine Y. Sbei N. Rahali S. Taha T. H. Boufahja F. Elfalleh W. Garzoli S. Bendif H. Slimane Ben Ali D. Enhanced environmental remediation through hybrid adsorption-photocatalysis using ZnO/TiO 2 -CaAlg composite catalysts. RSC Adv. 2026;16:8226–8242. doi: 10.1039/D5RA09465H. [DOI] [PMC free article] [PubMed] [Google Scholar]
  64. Cui W. Liang E. Cheng K. Hou Z. Li C. Liu Y. Cao S. Tian B. Ma C. Xu M. Wu P. Luo S. Liu S. Li W. Harnessing the synergistic dual role of lignin-derived blue carbon dots over TiO2 for highly efficient solar photocatalytic degradation of tetracycline. New J. Chem. 2026;50:7448–7458. doi: 10.1039/D6NJ00560H. [DOI] [Google Scholar]
  65. Samal P. Satpathy S. Rath G. Sabut T. Sahoo A. P. Arakha M. Lignin-Encapsulated ZnO Nano-Hybrids Exhibit Enhanced Antibacterial and Photocatalytic Activity via ROS-Mediated Oxidative Stress and Bacterial Membrane Disruption. ACS Omega. 2026;11(4):6133–6146. doi: 10.1021/acsomega.5c10788. https://dx.doi.org/10.1021/ACSOMEGA.5C10788 [DOI] [PMC free article] [PubMed] [Google Scholar]
  66. Dhayal A. Kumar H. Kumar G. Prakash S. Yadav A. Brahma M. Development of CuO-enhanced soybean protein isolate biofilms with antioxidant, photocatalytic, and antimicrobial properties for food packaging applications. Next Mater. 2025;8:100616. doi: 10.1016/j.nxmate.2025.100616. https://dx.doi.org/10.1016/J.NXMATE.2025.100616 [DOI] [Google Scholar]
  67. Le T. P. Tinh L. V. Pham P. Q. Le K. V. Tran N. Q. M. Mai N. X. D. Phan T. B. Nguyen L. M. T. Pham N. K. Synergistic enhancement of antibacterial and photocatalytic activity in green-synthesized chitosan stabilized multiphase CuxOy–ZnO composites. Mater. Sci. Eng., B. 2026;324:119060. doi: 10.1016/j.mseb.2025.119060. https://dx.doi.org/10.1016/J.MSEB.2025.119060 [DOI] [Google Scholar]
  68. Guo L. Wu R. Wei Y. Yao Z. Su X. Su Q. Yu J. TiO2-chitosan-cyclodextrin polymers based on subject-object recognition for adsorption-assisted photocatalytic degradation of Congo red. Int. J. Biol. Macromol. 2026;340:150156. doi: 10.1016/j.ijbiomac.2026.150156. https://dx.doi.org/10.1016/J.IJBIOMAC.2026.150156 [DOI] [PubMed] [Google Scholar]
  69. Rajeswari R. Thanikaikarasan S. Karthik P. Mukkannan A. Synergistic photocatalytic activity of MoS2/NiFe-LDH/cellulose acetate film toward the degradation of a pharmaceutical contaminant. Surf. Interfaces. 2026;87:108838. doi: 10.1016/j.surfin.2026.108838. https://dx.doi.org/10.1016/J.SURFIN.2026.108838 [DOI] [Google Scholar]
  70. Dhayal A. Kumar H. Prakash S. Kumar A. Brahma M. Maruthi M. Development of starch/whey protein isolate biofilm incorporated with silver oxide nanoparticles: A multifunctional antioxidant, antibacterial, photocatalytic, and anticancer agent. Inorg. Chem. Commun. 2025;171:113661. doi: 10.1016/j.inoche.2024.113661. https://dx.doi.org/10.1016/J.INOCHE.2024.113661 [DOI] [Google Scholar]
  71. Chen Z. Yan D. Wang X. Ding G. Wang Z. Xiao Y. Liu X. Wang P. Chen L. Shuai L. Liao G. Biochar-Tailored Carbon Nitride Enables Piezo-Photocatalytic H2O2 Production via Boosted Charge Transport. ACS Catal. 2025;15:13568–13580. doi: 10.1021/acscatal.5c02889. https://dx.doi.org/10.1021/ACSCATAL.5C02889 [DOI] [Google Scholar]
  72. Bai Z. K. Ge Q. M. Jiang N. Cong H. Zhang Y. Q. Liu M. Fan Y. Photocatalytic degradation of thiamethoxam with a ternary organic/inorganic composite triggered by cucurbit[7]uril-block. Mater. Chem. Phys. 2023;303:127653. doi: 10.1016/j.matchemphys.2023.127653. [DOI] [Google Scholar]
  73. Khor S. H. Lee M. L. Y. Basirun W. J. Juan J. C. Phang S. W. The effect of morphology of polyaniline on photodegradation of reactive black 5 dyes. Polym. Bull. 2023;81(8):7295–7327. doi: 10.1007/s00289-023-05056-1. [DOI] [Google Scholar]
  74. Ahmed A. Alabada R. Usman M. Alothman A. A. Tufail M. K. Mohammad S. Ahmad Z. Synthesis of visible-light-responsive lanthanum-doped copper ferrite/graphitic carbon nitride composites for the photocatalytic degradation of toxic organic pollutants. Diamond Relat. Mater. 2024;141:110630. doi: 10.1016/j.diamond.2023.110630. [DOI] [Google Scholar]
  75. Suhag M. H. Katsumata H. Tateishi I. Furukawa M. Kaneco S. Black Phosphorus-Doped Graphitic Carbon Nitride with Aromatic Benzene Rings for Efficient Photocatalytic Hydrogen Production. Langmuir. 2023;39:13121–13131. doi: 10.1021/acs.langmuir.3c01518. [DOI] [PubMed] [Google Scholar]
  76. Putri K. N. A. Chandratana V. Marlina L. A. Fongkaew I. Hutama A. S. Narkbuakaew T. Pangon A. Intasanta V. Ogawa M. Hoven V. P. Tailoring Alginate and Graphitic Carbon Nitride Hydrogel Geometries via 3D Printing for Efficient Photocatalytic Solar-Driven Hydrogen Evolution. ACS Appl. Polym. Mater. 2026;8:2432–2445. doi: 10.1021/acsapm.5c04634. [DOI] [Google Scholar]
  77. Shang Y. Zheng M. Liu H. Jin X. Yan C. Song L. Qi Z. Jing F. Song P. Zhou X. Chen G. Lv C. Mimicking Frustrated Lewis Pairs on Graphitic Carbon Nitride for CO2 Photoreduction. ACS Catal. 2023;13:14530–14539. doi: 10.1021/acscatal.3c03628. [DOI] [Google Scholar]
  78. Hu T. Sun T. Xue B. Wang X. Y. A near-infrared-responsive bismuth sulfide/polymeric carbon nitride/chitosan/polyacrylamide composite hydrogel and contactless food preservation application. Colloids Surf., A. 2025;727:138376. doi: 10.1016/j.colsurfa.2025.138376. [DOI] [Google Scholar]
  79. Gricius Z. Øye G. Pickering Emulsions Stabilized by Hybrid TiO2-pNIPAm Composites for the Photocatalytic Degradation of 4-Propylbenzoic Acid. ACS Omega. 2025;10:1988–2002. doi: 10.1021/acsomega.4c07847. https://dx.doi.org/10.1021/ACSOMEGA.4C07847 [DOI] [PMC free article] [PubMed] [Google Scholar]
  80. Wang Q. Zheng S. Ma W. Qian J. Huang L. Deng H. Zhou Q. Zheng S. Li S. Du H. Li Q. Hao D. Yang G. Facile synthesis of direct Z-scheme PPy/NH2-UiO-66 heterojunction for enhanced photocatalytic Cr(VI) reduction, industrial electroplating wastewater treatment, and tetracycline degradation. Appl. Catal. B Environ. Energy. 2024;344:123669. doi: 10.1016/j.apcatb.2023.123669. [DOI] [Google Scholar]
  81. Guo Q. Wei J. Yu S. Feng X. Gao Z. Wang R. Yu H. Ge Z. Yang W. Soft robots with different movement capabilities based on photo-responsive multilayer poly(N-isopropylacrylamide) and multi-walled carbon nanotubes. J. Colloid Interface Sci. 2025;690:137351. doi: 10.1016/j.jcis.2025.137351. [DOI] [PubMed] [Google Scholar]
  82. Chen X. Li Y. Xu L. Zhang D. Guan Y. Dong L. Bao M. Wang Z. Thermosensitive Microfibril Cellulose/MnO2 Membrane: Dual Network Structure, Photothermal Smart Modulation for Switchable Emulsion Separation. ACS Sustain. Chem. Eng. 2023;11:931–944. doi: 10.1021/acssuschemeng.2c05204. [DOI] [Google Scholar]
  83. Zhang D. Li C. Zhang G. Tian J. Liu Z. Phototunable and Photopatternable Polymer Semiconductors. Acc. Chem. Res. 2024;57(4):625–635. doi: 10.1021/acs.accounts.3c00750. [DOI] [PubMed] [Google Scholar]
  84. Liu M. Han X. Chen H. Peng Q. Huang H. A molecular descriptor of intramolecular noncovalent interaction for regulating optoelectronic properties of organic semiconductors. Nat. Commun. 2023;14(1):2500. doi: 10.1038/s41467-023-38078-4. [DOI] [PMC free article] [PubMed] [Google Scholar]
  85. Divya M. Cherukupally N. Gogoi S. K. Pradhan J. R. Mondal S. K. Jain M. Senyshyn A. Dasgupta S. Super Flexible and High Mobility Inorganic/Organic Composite Semiconductors for Printed Electronics on Polymer Substrates. Adv. Mater. Technol. 2023;8:2300256. doi: 10.1002/admt.202300256. [DOI] [Google Scholar]
  86. Dhanda E. Nain A. Dahiya S. A novel PANI@Er-doped ZnO (PEZ) MOFs: Synthesis, Characterization and highly efficient photocatalyst for degradation of Methylene Blue. Water, Air, Soil Pollut.: Focus. 2024;235(8):504. doi: 10.1007/s11270-024-07311-1. [DOI] [Google Scholar]
  87. Yu T. Liu L. Wang Y. Zhang S. Li L. Liang C. PI/TiC/TiO2 with Z-scheme heterostructure for the photocatalytic degradation of organic dyes. New J. Chem. 2023;47:21010–21023. doi: 10.1039/D3NJ04801B. https://dx.doi.org/10.1039/d3nj04801b [DOI] [Google Scholar]
  88. Liu J. Duan S. Feng X. Jiang Y. Xiao Y. Zhang W. Liu Y. Zhou E. Zhang J. Liu Z. Conductive Polymer-Inorganic Polythiophene/Cd0.5Zn0.5S Heterojunction with Apace Charge Separation and Strong Light Absorption for Boosting Photocatalytic Activity. Inorg. Chem. 2023;62:17241–17253. doi: 10.1021/acs.inorgchem.3c02444. [DOI] [PubMed] [Google Scholar]
  89. Li S. Wan H. Lin J. Min J. Physicochemical interactions between amorphous metal oxide and polymer in metal–polymer hybrid materials. Mater. Des. 2023;230:111993. doi: 10.1016/j.matdes.2023.111993. [DOI] [Google Scholar]
  90. Li N. Jabegu T. He R. Yun S. Ghosh S. Maraba D. Olunloyo O. Ma H. Okmi A. Xiao K. Wang G. Dong P. Lei S. Covalently-Bonded Laminar Assembly of Van der Waals Semiconductors with Polymers: Toward High-Performance Flexible Devices. Small. 2025;21:2310175. doi: 10.1002/smll.202310175. [DOI] [PubMed] [Google Scholar]
  91. Wu F. Fan L. Chen Y. Chen S. Shen J. Liu P. Crystallization of 2D TiO2 Nanosheets via Oriented Attachment of 1D Coordination Polymer. Nano Lett. 2024;25:56–62. doi: 10.1021/acs.nanolett.4c04084. [DOI] [PMC free article] [PubMed] [Google Scholar]
  92. Lunardi A. Bortolotto T. Nunes Cechin C. Daudt N. D. F. Mello M. D. A. dos Santos S. S. Cargnelutti R. Lang E. S. Tirloni B. Novel organically linked ZnII hydrogenselenite coordination polymers: synthesis, characterization, and efficient TiO2 photosensitization for enhanced photocatalytic hydrogen production. Dalton Trans. 2023;52:16841–16848. doi: 10.1039/D3DT03094F. https://dx.doi.org/10.1039/d3dt03094f [DOI] [PubMed] [Google Scholar]
  93. El Gohary H. G. Qahtan T. F. Alharbi H. G. Asnag G. M. Waly A. L. Studies of the Structural, Optical, Thermal, Electrical and Dielectric Properties of a Polyvinyl Alcohol/Sodium Alginate Blend Doped with Cu Nanoparticles and ZnO Nanorods as Hybrid Nanofillers for Use in Energy Storage Devices. J. Polym. Environ. 2023;31(7):2930–2940. doi: 10.1007/s10924-023-02785-2. [DOI] [Google Scholar]
  94. Coromelci C. G. Turcu E. Doroftei F. Palamaru M. N. Ignat M. Conjugated Polymer Modifying TiO 2 Performance for Visible-Light Photodegradation of Organics. Polymers. 2023:2805. doi: 10.3390/polym15132805. [DOI] [PMC free article] [PubMed] [Google Scholar]
  95. Hasi Q. M. Yu J. Guo Y. Hu S. Jiang S. Xiao C. Li A. Chen L. Study on photocatalytic degradation and antibacterial properties of conjugated microporous polymers/TiO2 composite membranes. J. Colloid Interface Sci. 2025;679:811–823. doi: 10.1016/j.jcis.2024.10.029. [DOI] [PubMed] [Google Scholar]
  96. Khan W. U. Khan S. U. Khan S. U. Gul A. Zaman H. Khan W. U. Ali N. Aziz A. Khan M. I. Khan D. Gouda M. M. Carboxymethyl-cellulose/starch/copper-oxide nanocomposite hydrogel green synthesis for organic pollutants photocatalytic degradation that supports health applications. Colloids Surf., A. 2025;718:136919. doi: 10.1016/j.colsurfa.2025.136919. [DOI] [Google Scholar]
  97. Pourkodee D. Renuka Devee D. Sailatha E. Synthesis and photocatalytic efficiency of novel ZnO-CBS-Ni complex for diclofenac sodium under irradiation of light. Inorg. Chem. Commun. 2025;171:113585. doi: 10.1016/j.inoche.2024.113585. [DOI] [Google Scholar]
  98. Han D. Wang L. Wang C. Effect of in situ synthesis reaction of methacrylic acid (MAA)/zinc oxide (ZnO) on frictional wear of metals during compounding. Surf. Coat. Technol. 2024;476:130213. doi: 10.1016/j.surfcoat.2023.130213. [DOI] [Google Scholar]
  99. Elsayed H. Mohamed G. Sultan M. A Synergistic High-Performance Hydrogel Adsorbent: NiO-g-C3N4@ALG-g-PAA for Efficient Methylene Blue Adsorption. Colloids Surf., A. 2026;748:141009. doi: 10.1016/j.colsurfa.2026.141009. [DOI] [Google Scholar]
  100. Zhang H. Tang P. Yang K. Wang Q. Feng W. Tang Y. PAA/TiO2@C composite hydrogels with hierarchical pore structures as high efficiency adsorbents for heavy metal ions and organic dyes removal. Desalination. 2023;558:116620. doi: 10.1016/j.desal.2023.116620. https://dx.doi.org/10.1016/J.DESAL.2023.116620 [DOI] [Google Scholar]
  101. Li R. Xiao G. Chen C. Chen C. Hu X. Li Y. Yang Z. Shang S. Wang M. Self-assembly graphene oxide membrane embedded with CPU@PAA@TiO2 for enhancing the dyes separation and photocatalytic self-cleaning performance. J. Membr. Sci. 2023;683:121816. doi: 10.1016/j.memsci.2023.121816. [DOI] [Google Scholar]
  102. Turkten N. Karatas Y. Uyguner-Demirel C. S. Bekbolet M. Preparation of PANI modified TiO2 and characterization under pre- and post- photocatalytic conditions. Environ. Sci. Pollut. Res. 2023;30(51):111182–111207. doi: 10.1007/s11356-023-30090-x. [DOI] [PubMed] [Google Scholar]
  103. Kumar A. Raorane C. J. Syed A. Bahkali A. H. Elgorban A. M. Raj V. Kim S. C. Synthesis of TiO2, TiO2/PAni, TiO2/PAni/GO nanocomposites and photodegradation of anionic dyes Rose Bengal and thymol blue in visible light. Environ. Res. 2023;216:114741. doi: 10.1016/j.envres.2022.114741. [DOI] [PubMed] [Google Scholar]
  104. Arslan-Alaton I. Koba-Ucun O. Bekbolet M. Turkten N. Karatas Y. On the toxicity behaviour of composite polyaniline-zinc oxide photocatalytic nanoparticles and their surrogate chemicals. Appl. Catal., A. 2023;659:119199. doi: 10.1016/j.apcata.2023.119199. [DOI] [Google Scholar]
  105. Liu B. Zhang J. Li H. Cheng B. Bie C. MOF-derived ZnO/PANI S-scheme heterojunction for efficient photocatalytic phenol mineralization coupled with H2O2 generation. Acta Phys. Chim. Sin. 2025;41:100121. doi: 10.1016/j.actphy.2025.100121. [DOI] [Google Scholar]
  106. Khan F. Zahid M. Bhatti H. N. Jamil Y. Degradation of persistent organic pollutant using Ag-doped ZnO-ZnS–polyaniline composite as photocatalyst. Int. J. Environ. Sci. Technol. 2022;20(5):4811–4826. doi: 10.1007/s13762-022-04283-9. [DOI] [Google Scholar]
  107. Kermia A. E. B. Cherik D. Belhamdi B. Fouial-Djebbar D. Özacar M. Trari M. Solar-light-driven photocatalytic degradation of diclofenac via polyaniline/ZnO nano-composite photocatalysts. J. Dispersion Sci. Technol. 2025:1–11. doi: 10.1080/01932691.2025.2556677. [DOI] [Google Scholar]
  108. Dhanda E. Nain A. Dahiya S. A highly effective PANI@(Ce-Er) dual doped ZnO (PCEZ) nanocomposite as UV-light driven photocatalyst for degradation of MB dye: synthesis and characterization. Phys. Scr. 2024;99:085043. doi: 10.1088/1402-4896/ad635a. [DOI] [Google Scholar]
  109. Haspulat Taymaz B. A novel Ppy/ZnO@Co ternary nanocomposite with enhanced visible light-driven photocatalytic performance. J. Taiwan Inst. Chem. Eng. 2023;144:104741. doi: 10.1016/j.jtice.2023.104741. [DOI] [Google Scholar]
  110. Kavyashree D. Mahendra K. Gopal K. Sunitha D. V. Next-generation PPy/ZnO nanocomposites: In situ synthesis and enhanced visible-light-driven photocatalytic degradation of organic pollutants and detection of dopamine. Opt. Mater. 2026;170:117711. doi: 10.1016/j.optmat.2025.117711. [DOI] [Google Scholar]
  111. Faniband B. Chandra S. S. Hiremath A. Pattar J. Sreekanth R. Mahendra K. Manohara S. R. Rao H. N. A. Nataraja S. K. Enhanced charge transport and interfacial polarization in PANI/SnO2 nanocomposites. Mater. Sci. Eng., B. 2026;323:118792. doi: 10.1016/j.mseb.2025.118792. [DOI] [Google Scholar]
  112. Pal S. Das P. S. Naskar M. K. Ghosh S. Metal oxide nanocrystals embedded polypyrrole nanohybrid: Exploring role of interface in photocatalytic hydrogen generation. Mater. Today Sustain. 2024;25:100610. doi: 10.1016/j.mtsust.2023.100610. [DOI] [Google Scholar]
  113. Nagaraja M. Prashanth S. Mokshanatha P. B. Pattar J. Manohara S. R. Sunil K. Tuning electrical conductivity and dielectric properties of chitosan/polyaniline by doping with varying concentration of Nb2O5 nanoparticles. Solid State Ion. 2026;437:117129. doi: 10.1016/j.ssi.2026.117129. [DOI] [Google Scholar]
  114. Nayab M. Farhan A. Zahid M. Rehan Z. A. Jilani A. Almeer R. Ibrahim H. Al-Zaqri N. Solar-Driven Photocatalytic Degradation of Organic Pollutants by I-MnO2/PTh Nanocomposite: Mechanisms, Kinetics, and Implications for Advanced Environmental Remediation. Int. J. Environ. Res. 2025;20(1):48. doi: 10.1007/s41742-025-01012-1. [DOI] [Google Scholar]
  115. Chowdhury M. S. H. Rahman Khan M. M. Shohag M. R. H. Rahman S. Paul S. K. Rahman M. M. Asiri A. M. Rahman M. M. Easy synthesis of PPy/TiO2/ZnO composites with superior photocatalytic performance, efficient supercapacitors and nitrite sensor. Heliyon. 2023;9(9):e19564. doi: 10.1016/j.heliyon.2023.e19564. [DOI] [PMC free article] [PubMed] [Google Scholar]
  116. Yan H. Xiong J. Du P. Wu E. Pan T. Li N. Construction of ZnO/PPy/PAN Nanofiber Membrane as Heterojunction Photocatalyst with Enhanced Photocatalytic Activity. Fibers Polym. 2025;26:589–596. doi: 10.1007/s12221-024-00839-3. [DOI] [Google Scholar]
  117. Abdi Z. Bagheri O. Kazemzadehhojaghan M. Malek Khachatourian A. In situ synthesis of polypyrrole/Nd-doped ZnO nanocomposite with enhanced visible light photocatalytic performance for the degradation of organic dyes. Mater. Chem. Phys. 2023;296:127248. doi: 10.1016/j.matchemphys.2022.127248. [DOI] [Google Scholar]
  118. Arif M. Core-shell systems of crosslinked organic polymers: a critical review. Eur. Polym. J. 2024;206:112803. doi: 10.1016/j.eurpolymj.2024.112803. [DOI] [Google Scholar]
  119. Alresheedi N. M. Ghitas A. Almutairi F. N. Shahat M. A. Optimizing the Efficiency of Polymer Solar Cells Based on Core-Shell PAni@ZnO Composites Utilizing Argon Plasma Treatment. J. Inorg. Organomet. Polym. Mater. 2024;35(1):123–140. doi: 10.1007/s10904-024-03214-0. [DOI] [Google Scholar]
  120. Saadat M. Yamini Y. PPy@ZnO@NiCo-LDH core-shell nanostructures grown on pencil lead as a novel layer-by-layer assembly fiber coating for enhanced extraction of PAHs from water samples. Microchem. J. 2025;218:115759. doi: 10.1016/j.microc.2025.115759. [DOI] [Google Scholar]
  121. Hastuti L. P. Kusumaatmaja A. Darmawan A. Kartini I. Photocatalytic membrane of TiO2/CNT decorated PAN nanofibers with enhanced performance under LED visible-light irradiation. Energy Environ. 2023;34:2364–2385. doi: 10.1177/0958305X221108494. [DOI] [Google Scholar]
  122. Yadav M. Arora R. Dhanda M. Ahlawat S. Shoran S. Ahlawat S. Nehra S. P. Singh G. Lata S. Ppy/TiO2-SiO2 nanohybrid series: synthesis, characterization, photocatalytic activity, and antimicrobial potentiality. J. Environ. Health Sci. Eng. 2023;21(1):239–254. doi: 10.1007/s40201-023-00858-x. [DOI] [PMC free article] [PubMed] [Google Scholar]
  123. Sawut A. Wu T. Simayi R. Jiao X. Feng Y. Preparation and Photocatalytic Performance of Sodium Alginate/Polyacrylamide/Polypyrrole-TiO2 Nanocomposite Hydrogels. Polymers. 2023;15:4174. doi: 10.3390/polym15204174. [DOI] [PMC free article] [PubMed] [Google Scholar]
  124. Omar R. A. Radwan E. K. Salih S. A. Mohamed G. G. Synergistic adsorption–photocatalytic degradation of the emerging contaminant hydroxybenzotriazole by a 3D sponge-like easy separation polypyrrole/TiO2 composite. Appl. Water Sci. 2024;14(10):229. doi: 10.1007/s13201-024-02284-2. [DOI] [Google Scholar]
  125. Joseph R. Padmanaban A. Ida S. Wilson P. Efficient Degradation of 2,4-D by TIO2-rGO-PANI-PPy Nanocomposite Photocatalyst under Visible Light Irradiation: Mechanisms and Degradation Pathways. ChemistrySelect. 2025;10:e202405563. doi: 10.1002/slct.202405563. [DOI] [Google Scholar]
  126. Sura A. Singh A. Narwal S. Singh A. Sehrawat V. Dahiya B. Kumar V. Sharma U. Phor L. Nain S. Khanna V. Harnessing Synergy in g-C3N4/ZnO/PPy Nanocomposite for Efficient Photocatalytic Degradation of Phenolic and Antibiotic Pollutants. J. Nanotechnol. 2025;2025:8823568. doi: 10.1155/jnt/8823568. [DOI] [Google Scholar]
  127. Heltina D. Yoselino D. Dumaria A. Amila K. Sembiring M. P. Amri A. Jiang Z. T. Fabrication and Photocatalytic Performance of ZnO-Biochar Composites for Eliminating Dye Waste. Commun. Sci. Technol. 2025;10:302–312. doi: 10.21924/cst.10.2.2025.1795. [DOI] [Google Scholar]
  128. Rokonujjaman M. Ahmad M. F. Parvin S. Abir A. Y. Suhag M. H. Rahman Khan M. M. Jeong J. H. Facile Synthesis of PPy-V2O5-AgI Composites for Efficient Photocatalysts and Effective Supercapacitors: Toward the Promise of Highly Reusable Performance and Morphological Topography. Polym. Compos. 2026;47:579–596. doi: 10.1002/pc.70168. [DOI] [Google Scholar]
  129. Alorabi A. Q. Sustainable Synthesis of PPHC@TiO2/PPy Composite for Enhanced Congo Red Dye Removal: Kinetics, Isotherms, and Mechanistic Insights. J. Cluster Sci. 2025;36(5):169. doi: 10.1007/s10876-025-02898-9. [DOI] [Google Scholar]
  130. John Christopher J. Rajkumar S. Sharmila Lydia I. Princy Merlin J. Investigation of Fe2(MoO4)3@Ppy Composite for Effective Photocatalytic Degradation of Crystal Violet Under Visible Light. J. Inorg. Organomet. Polym. Mater. 2025;35(9):7312–7330. doi: 10.1007/s10904-025-03745-0. [DOI] [Google Scholar]
  131. Sudapalli A. M. Tripathy S. Shimpi N. Hierarchically structured PAN/g-C3N4/ZnO hybrid nanofibers for photocatalytic degradation of hazardous ionic dyes. Diamond Relat. Mater. 2026;162:113309. doi: 10.1016/j.diamond.2026.113309. [DOI] [Google Scholar]
  132. Suo R. Xie L. Liao J. Chen J. Lu C. Z. Enhanced Charge Separation in a PAN/ZnO Nanocomposite for Promoted Photocatalytic Hydrogen Evolution. ACS Appl. Energy Mater. 2024;7:5668–5678. doi: 10.1021/acsaem.4c00521. [DOI] [Google Scholar]
  133. Lad A. R. Bodkhe G. A. Raut S. D. Botewad S. N. Waghule N. N. In situ synthesized PPY@CuO–NiO ternary nanocomposite for high-performance pseudocapacitors. J. Appl. Electrochem. 2026;56(1):20. doi: 10.1007/s10800-025-02413-y. [DOI] [Google Scholar]
  134. Chowdhury M. S. H. Rahman Khan M. M. Deb B. Shohag M. R. H. Rahman S. Rahman M. M. Alzahrani K. A. Rahman M. M. Bhuyan M. M. Jeong J. H. Fabrication of Poly(Ani-co-Py)/NiO Composites with Superb Photocatalytic Performance and Effective p-Nitrophenol Sensor. J. Inorg. Organomet. Polym. Mater. 2025;35:1322–1335. doi: 10.1007/s10904-024-03340-9. [DOI] [Google Scholar]
  135. Rani L. Chauhan R. P. Antibacterial Activity of Solvothermally Synthesized PVP/EDTA Encapsulated Zinc Sulphide Nanoparticles Embedded in Polyacrylonitrile (PAN) Electrospun Nanofibers. J. Cluster Sci. 2022;34(4):1789–1804. doi: 10.1007/s10876-022-02353-z. [DOI] [Google Scholar]
  136. Tyagi N. Ashraf W. Mittal H. Fatima T. Khanuja M. Singh M. K. A facile synthesis of ternary hybrid nanocomposite of WS2/ZnO/PPy: An efficient photocatalyst for the degradation of chromium hexavalent. Dyes Pigm. 2023;210:110998. doi: 10.1016/j.dyepig.2022.110998. [DOI] [Google Scholar]
  137. Omer R. A. Azeez Y. H. Sultan H. K. I. Ismail H. K. Hamasdiq A. F. Kareem R. O. Synthesis and DFT-guided evaluation of PPy-ZnFe2O4@Fe3O4 nanocomposite for pharmaceutical adsorption. J. Phys. Chem. Lett. 2025;6:240–255. doi: 10.22034/jchemlett.2025.554966.1361. [DOI] [Google Scholar]
  138. Anand A. Aneggi E. Boaretti C. Lorenzetti A. Trovarelli A. Modesti M. Roso M. Boosting the photocatalytic performance of PAN-TiO2 nanostructured membranes by mechanosynthesis. J. Environ. Chem. Eng. 2024;12:111595. doi: 10.1016/j.jece.2023.111595. [DOI] [Google Scholar]
  139. Hastuti L. P. Kusumaatmaja A. Darmawan A. Kartini I. Durable photocatalytic membrane of PAN/TiO2/CNT for methylene blue removal through a cross-flow membrane reactor. Sep. Sci. Technol. 2023;58:704–720. doi: 10.1080/01496395.2022.2145221. [DOI] [Google Scholar]
  140. Mousavi S. M. Rahmani M. B. Enhanced Photocatalytic Performance of Semicrystalline Cl-Doped PPy@TiO2 Nanocomposites for MB Degradation. Polym. Adv. Technol. 2025;36:e70312. doi: 10.1002/pat.70312. [DOI] [Google Scholar]
  141. Shashikala K. J. Kalleshappa C. M. Jagadeesh M. R. Almalki A. S. A. Alsanie W. F. Alhadharami A. Polypyrrole-Integrated Mg-ZnO Nanocomposites: A Dual-Functional Material for Photocatalytic RhB Degradation and Electrochemical Sensing. J. Appl. Polym. Sci. 2026;143:e58002. doi: 10.1002/app.58002. [DOI] [Google Scholar]
  142. Revathi R. Shanmugam R. Latha S. Mounica P. Arivazhagan G. Polypyrrole, Zinc oxide, and Nickel oxide ternary nanocomposite: Synthesis, characterization, and photocatalytic activity on methylene blue, and methyl orange dye. Solid State Commun. 2025;405:116159. doi: 10.1016/j.ssc.2025.116159. [DOI] [Google Scholar]
  143. Raut S. Patro A. Dhal S. Sahoo S. K. Green synthesized ZnO-Ag functionalized electrospun PAN nanofibers for efficient crystal violet dye removal: A combined experimental and computational approach. Nano-Struct. Nano-Objects. 2026;45:101598. doi: 10.1016/j.nanoso.2025.101598. [DOI] [Google Scholar]
  144. Arya K. Joshi D. P. Rawat P. S. Removal of Heavy Metals and Cationic Dye Simultaneously From Polluted Water by Polypyrrole/TiO2 Nanocomposite. J. Appl. Polym. Sci. 2025;142:e57622. doi: 10.1002/app.57622. [DOI] [Google Scholar]
  145. Nazir M. K. Javaid S. Afzal H. Taj M. B. Baamer D. F. Almasoudi A. Aldahiri R. H. Ali O. M. Khan M. I. Ahmed M. M. Shanableh A. Fernandez-Garcia J. Synthesis, Magnetic, and Photocatalytic Activity of Polypyrrole-Based TiO2–Fe Catalyst for Wastewater Treatment. Catalysts. 2024;14:692. doi: 10.3390/catal14100692. [DOI] [Google Scholar]
  146. He Z. Wu Y. Li N. Lai H. Liu B. Jin T. Pickering emulsion-based TiO2@PPy janus microspheres for efficient photocatalytic degradation of 5-methylbenzotriazole. J. Alloys Compd. 2023;960:170335. doi: 10.1016/j.jallcom.2023.170335. [DOI] [Google Scholar]
  147. Grandcolas M. Double-Sided Illuminated Electrospun PAN TiO2-Cu2O Membranes for Enhanced CO2 Photoreduction to Methanol. Catalysts. 2026;16:107. doi: 10.3390/catal16010107. [DOI] [Google Scholar]
  148. Hastuti L. P. Budiman A. H. Darsono N. Timuda G. E. Bakri A. Darmawan A. Arjasa O. P. Novel g-C3N4/rGO/NiS incorporated into GO free-standing membrane as a photocatalytic membrane for excellent dye photodegradation. Fullerenes, Nanotubes, Carbon Nanostruct. 2025;33:1292–1305. doi: 10.1080/1536383X.2025.2499184. [DOI] [Google Scholar]
  149. Ghosh S. Das P. S. Sarkar D. Pal S. Naskar M. K. Chaudhary Y. S. Dey S. Sinha C. Z-Scheme Heterostructures Using Band-Gap-Tunable ZnO by Metal Doping and Coupling with Polypyrrole for Enhanced Photocatalytic Water Splitting. ACS Appl. Polym. Mater. 2023;5:9918–9930. doi: 10.1021/acsapm.3c01757. [DOI] [Google Scholar]
  150. Loyalka S. Dangi S. B. Hashmi S. Z. Choudhary B. L. Dalela S. Quraishi A. M. Kumar S. Aakansha Ahmad M. A. Alvi P. A. Improved functional properties of unique and novel PVDF/Ppy/ZnO (PPZ) polymer nanocomposites. Compos. Interfaces. 2025;33:641–658. doi: 10.1080/09276440.2025.2546177. [DOI] [Google Scholar]
  151. Ali Hosseini Moradi S. Enhanced photocatalytic removal of tetracycline by ZnO/NiCo2O4 through the construction of a p–n heterojunction. Chem. Phys. 2024;587:112396. doi: 10.1016/j.chemphys.2024.112396. [DOI] [Google Scholar]
  152. De S. Dey A. De S. K. Effective move of Polypyrrole/TiO2 hybrid nanocomposites on removal of methylene blue dye by photocatalytic activity. Chem. Phys. Impact. 2024;9:100723. doi: 10.1016/j.chphi.2024.100723. https://dx.doi.org/10.1016/j.ssc.2006.01.027 [DOI] [Google Scholar]
  153. Senthilkumar K. Krishnan H. Synthesis and performance evaluation of polypyrrole/titanium oxide composite as an electrocatalyst for simultaneous power generation and wastewater treatment in bioelectrochemical systems. Biomass Convers. Biorefinery. 2024;15(22):28605–28615. doi: 10.1007/s13399-024-05556-8. [DOI] [Google Scholar]
  154. Effati E. Behmaram K. Shokri E. Enhanced Cleaning Efficiency of PVC Membrane by ZnO–PPy Electrically Conductive Composite in Oily Wastewater Treatment. J. Appl. Polym. Sci. 2025;142:e57697. doi: 10.1002/app.57697. [DOI] [Google Scholar]
  155. Bharti C. Singh A. Vidivay Baghel S. Nandan K. Revitalizing Battery Waste: Unveiling Ni/PPy/TiO2-Nanocomposites for Dye Degradation. Chem. Afr. 2026;9(2):114. doi: 10.1007/s42250-026-01595-y. [DOI] [Google Scholar]
  156. Xu J. Hou T. Zhou J. Ye H. Wang Y. Cheng L. Li X. Yang B. Hydrophilic, self-cleaning, and recyclable La-TiO2/PAN nanofibrous membranes rapidly fabricated via electro-centrifugal spinning for photocatalytic organic pollutants. Appl. Surf. Sci. 2024;672:160806. doi: 10.1016/j.apsusc.2024.160806. [DOI] [Google Scholar]
  157. Xu H. Fan P. Xu L. CuO/ZnO/CQDs@PAN Nanocomposites with Ternary Heterostructures for Enhancing Photocatalytic Performance. Catalysts. 2023;13:110. doi: 10.3390/catal13010110. [DOI] [Google Scholar]
  158. Sun H. Wu M. He D. Luo Y. Shang W. Jiang Y. Liu M. Zeng M. Wang N. Jia Z. Titanium dioxide@polyoxometalate-organic framework as an efficient photocatalyst for dye degradation under visible light conditions. Polyoxometalates. 2025:9140089. doi: 10.26599/POM.2025.9140089. [DOI] [Google Scholar]
  159. Liu H. Xie L. Suo R. Li W. Luo L. Chen J. Lu C. Z. Efficient Z scheme-type II charge transfer on the interfaces of PAN/ZnO/CdIn2S4 for the enhanced photocatalytic hydrogen generation. Int. J. Hydrogen Energy. 2024;63:36–47. doi: 10.1016/j.ijhydene.2024.03.136. [DOI] [Google Scholar]
  160. Moosaviyan S. A. Baezzat M. R. Ghaedi M. Abbasi-Asl H. Photocatalytic decomposition of methylene blue and rhodamine B using Ag–Ag2SeO3/Ppy nano-photocatalyst from aqueous solutions: experimental design optimization. J. Nanostructure Chem. 2023;14(6):419–436. doi: 10.1007/s40097-023-00531-7. [DOI] [Google Scholar]
  161. Quy B. M. Nguyen V. D. Hoa N. T. H. Linh N. T. N. Tung V. Q. Thapphanya S. Phuong N. N. Ha L. T. Nghia N. T. Synergistic photocatalytic removal of moxifloxacin from aqueous solutions using ZnO-Fe3O4-chitosan composites. Mater. Res. Express. 2024;11:055509. doi: 10.1088/2053-1591/ad45b8. [DOI] [Google Scholar]
  162. Denada L. Hariani P. L. Rachmat A. Synthesis and Characterization Composite Fe3O4/Chitosan-PVA/TiO2 for Photocatalytic Degradation of Tetracycline. J. Pure Appl. Chem. Res. 2025;14:39–50. doi: 10.21776/ub.jpacr.2025.014.03.7945. [DOI] [Google Scholar]
  163. Mancuso A. Vaiano V. Antico P. Sacco O. Venditto V. Photoreactive polymer composite for selective oxidation of benzene to phenol. Catal. Today. 2023;413–415:113914. doi: 10.1016/j.cattod.2022.09.020. [DOI] [Google Scholar]
  164. Salomatina E. Shelud’ko P. Kuz’michev V. Smirnova L. Photocatalytic Decomposition of Azo Dyes and Phenols Using Polymer Composites Containing Nanostructured Poly(Titanium Oxide) Doped with Gold or Silver Nanoparticles under Light Irradiation in a Wide Wavelength Range. Catalysts. 2023;13:423. doi: 10.3390/catal13020423. [DOI] [Google Scholar]
  165. Li W. Chen Z. Yang S. Cui K. Zhou X. Li H. Ma F. Wang W. Zhang Q. Zhang H. Enhanced Photocatalytic Degradation of Phenol by Electron-Directed Movement of Polypyrrole/ZnIn2S4 Composites. Ind. Eng. Chem. Res. 2024;63:8111–8121. doi: 10.1021/acs.iecr.4c00232. [DOI] [Google Scholar]
  166. Xie Y. Wang X. Li H. Wang T. Feng W. Li J. PAN/TiO2 Ultrafiltration Membrane for Enhanced BSA Removal and Antifouling Performance. Catalysts. 2023;13:320. doi: 10.3390/catal13020320. https://dx.doi.org/10.3390/catal13101320 [DOI] [Google Scholar]
  167. Elshahawy M. F. Ahmed N. A. Gad Y. H. Ali A. E.-H. Efficient photocatalytic remediation of lerui acid brilliant blue dye using radiation- prepared carboxymethyl cellulose/acrylic acid hydrogel supported by ZnO@Ag. Int. J. Biol. Macromol. 2024:129946. doi: 10.1016/j.ijbiomac.2024.129946. https://dx.doi.org/10.1016/J.IJBIOMAC.2024.129946 [DOI] [PubMed] [Google Scholar]
  168. Ghosh S. Bera S. Sardar S. Pal S. Camargo F. V. A. D'Andrea C. Cerullo G. Role of Efficient Charge Transfer at the Interface between Mixed-Phase Copper-Cuprous Oxide and Conducting Polymer Nanostructures for Photocatalytic Water Splitting. ACS Appl. Mater. Interfaces. 2023;15:18867–18877. doi: 10.1021/acsami.3c00090. [DOI] [PubMed] [Google Scholar]
  169. Li Y. Wan S. Liang W. Cheng B. Wang W. Xiang Y. Yu J. Cao S. D–A Conjugated Polymer/CdS S-Scheme Heterojunction with Enhanced Interfacial Charge Transfer for Efficient Photocatalytic Hydrogen Generation. Small. 2024;20:2312104. doi: 10.1002/smll.202312104. [DOI] [PubMed] [Google Scholar]
  170. Zhu X. Chen C. Shi Y. Wang J. Wang Y. Pan L. Guan Z. Dual-functional, highly efficient CaIn2S4/PDA@SnO2 photocatalyst with Z-Scheme for photocatalytic hydrogen production from water splitting and organic pollutant degradation. J. Alloys Compd. 2024;976:173151. doi: 10.1016/j.jallcom.2023.173151. [DOI] [Google Scholar]
  171. Wang M. Zhang G. Dong S. Li N. Xu Q. Li H. Lu J. Chen D. Optimizing Adsorption-Redox Sites and Charge Transfer of Ternary Polymer Photocatalyst with P–N Linkage for CO2 Conversion Coupled with Antibiotics Removal. Adv. Funct. Mater. 2024;34:2406516. doi: 10.1002/adfm.202406516. [DOI] [Google Scholar]
  172. Dong J. Zhao J. Yan X. Li L. Liu G. Ji M. Wang B. She Y. Li H. Xia J. Construction of carbonized polymer dots/potassium doped carbon nitride nanosheets Van der Waals heterojunction by ball milling method for facilitating photocatalytic CO2 reduction performance in pure water. Appl. Catal. B Environ. Energy. 2024;351:123993. doi: 10.1016/j.apcatb.2024.123993. [DOI] [Google Scholar]
  173. Aouadi A. Hamada Saud D. Rebiai A. Achouri A. Benabdesselam S. Mohamed Abd El-Mordy F. Pohl P. Ahmad S. F. Attia S. M. Abulkhair H. S. Ararem A. Messaoudi M. Introducing the antibacterial and photocatalytic degradation potentials of biosynthesized chitosan, chitosan–ZnO, and chitosan–ZnO/PVP nanoparticles. Sci. Rep. 2024;14(1):14753. doi: 10.1038/s41598-024-65579-z. [DOI] [PMC free article] [PubMed] [Google Scholar]
  174. Quy B. M. Thu N. T. N. Xuan V. T. Hoa N. T. H. Linh N. T. N. Tung V. Q. Le V. T. T. Thao T. T. Ngan N. T. K. Tho P. T. Hung N. M. Ha L. T. Photocatalytic degradation performance of a chitosan/ZnO–Fe3O4 nanocomposite over cationic and anionic dyes under visible-light irradiation. RSC Adv. 2025;15:1590–1603. doi: 10.1039/D4RA08262A. [DOI] [PMC free article] [PubMed] [Google Scholar]
  175. Afzal S. Naeem R. Sherino B. Nabi N. Behlil F. Julkapli N. M. Impact of chitosan on CS/TiO2 composite system for enhancing its photocatalytic performance towards dye degradation. Desalin. Water Treat. 2023;283:274–279. doi: 10.5004/dwt.2023.29229. [DOI] [Google Scholar]
  176. Reinehr I. L. Capra D. F. Kempka A. P. Visioli L. J. Paulino A. T. Enzweiler H. Innovative chitosan/TiO2 composite membrane for the sustainable photocatalytic purification of water contaminated with emerging micropollutants. Polym. Bull. 2025;82(14):9513–9533. doi: 10.1007/s00289-025-05921-1. [DOI] [Google Scholar]

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Data Availability Statement

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