Review Article
Microbial Lytic Polysaccharide Monooxygenases: Production, Purification and Bio-Industrial Applications: A Comprehensive Review
Syeda Quratulain Gillani*, Aliya Jabbar, Fareed Ahmed, Asma Nadeem, Maham Sabir and Sheza Fatima Bajwa
Department of Biotechnology, University of Sialkot, Sialkot, Pakistan.
Abstract | Lytic polysaccharide monooxygenases EC 1.14.99 are copper-dependent oxidative enzymes that play an essential role in the degradation of highly recalcitrant polysaccharides such as cellulose and chitin. They are widely distributed in fungi, bacteria and some marine organisms where they are secreted extracellularly. During degradation, LPMOs activate oxygen species at the copper center and introduce oxidation at specific positions of polysaccharide chains leading to chain disruption and significantly increasing the efficiency of overall biomass conversion. These enzymes play a major role in petrochemical industry especially in biofuel production. Moreover, it facilitates the conversion of lignocellulosic biomass into fermentable sugars so the use of these enzymes in food processing aid in the production of value-added materials such as nanocellulose and oligosaccharides.
Received | May 12, 2026; Accepted | June 18, 2026; Published | June 26, 2026
*Correspondence | Syeda Quratulain Gillani, Department of Biotechnology, University of Sialkot, Sialkot, Pakistan; Email: [email protected]
Citation | Gillani, S.Q., A. Jabbar, F. Ahmed, A. Nadeem, M. Sabir and S.F. Bajwa. 2026. Microbial lytic polysaccharide monooxygenases: production, purification and bio-industrial applications: A comprehensive review. Biologia (Lahore), 72(1): 43-54.
DOI | https://dx.doi.org/10.17582/journal.biologia/2026/72.1.43.54
Keywords | Lytic polysaccharide monooxygenases LPMOs, Depolymerize, Oxidative, Biomass, Biofuel, Microbial, Fermentation, Hydrolysis
Copyright: 2026 by the authors. Licensee ResearchersLinks Ltd, England, UK.
This article is an open access article distributed under the terms and conditions of the Creative Commons Attribution (CC BY) license (https://creativecommons.org/licenses/by/4.0/).
Introduction
Lytic Polysaccharide Monooxygenases (LPMOs) are formally included in the copper-dependent oxidative enzyme class known as the enzyme commission group EC 1.14.99. These biocatalysts are classified into a number of Auxiliary Activity (AA) families, specifically ranging from AA9 to AA17. Each AA family has evolved to be more adept at substrates like cellulose, chitin, or starch than others. The “histidine brace” motif, a structural feature in which a single copper ion is coordinated by two conserved histidine residues to drive catalysis, is the hallmark of these families at the molecular level. While members of some families, such as AA9 and AA16, primarily target cellulose, members of other families, such as AA10 and AA11, are necessary for shredding resilient chitin structures.
Auxiliary Activity families of LPMOs comprise a diverse group of copper-dependent oxidative enzymes that enhance the degradation of recalcitrant polysaccharides by oxidatively cleaving glycosidic bonds. Based on sequence similarity and substrate specificity, LPMOs are classified in the CAZy database into eight AA families: AA9, AA10, AA11, AA13, AA14, AA15, AA16 and AA17. The AA9 family is predominantly found in fungi and acts mainly on cellulose, catalyzing oxidation at the C1 or C4 carbon positions to improve cellulose accessibility for cellulases. AA10 enzymes occur primarily in bacteria but are also present in archaea, viruses and some fungi. They exhibit broader substrate specificity acting on chitin, cellulose and xylan (Vu et al., 2014). The fungal AA11 family consists mainly of chitin-active LPMOs involved in chitin degradation and cell-wall remodeling. AA13 enzymes are unique among LPMOs because they target starch facilitating oxidative starch depolymerization and enhancing the action of amylolytic enzymes (Loleggio et al., 2015). The AA14 family acts on xylan associated with plant cell walls thereby increasing the accessibility of cellulose within lignocellulosic biomass. AA15 LPMOs are widespread among insects, other animals, algae, oomycetes and some viruses where they participate in chitin and cellulose degradation and various biological processes such as molting and biomass digestion (Forseberg et al., 2011). AA16 represents a more recently identified fungal family that is mainly associated with cellulose oxidation and acts synergistically with cellulases during biomass conversion. The newest family AA17 has been identified predominantly in oomycetes and is distinguished by its activity on pectin significantly expanding the known substrate range of LPMOs beyond cellulose, chitin and starch (Couturier et al., 2018; Sabbadin et al., 2018). Collectively, these families demonstrate their crucial role in the enzymatic deconstruction of complex polysaccharides for both natural carbon cycling and industrial biorefinery applications (Li et al., 2019; Wang et al., 2022; Zhang et al., 2023).
Structure of LPMO enzymes
LPMOs are a highly diverse family of enzymes in terms of sequence, but they share a highly conserved 3D structure primarily composed of a β-sandwich fold placing the catalytic copper in a surface position (Frandsen et al., 2021).
In LPMOs, the histidine brace motif is the distinguishing feature where the N-terminal histidine and an internal histidine coordinate a single copper ion. Oxygen activation for oxidative polysaccharide cleavage requires the copper center, and recent studies have elucidated several active site configurations that allow for this unique enzymatic function. The catalytic surface of LPMOs are generally flat and contain aromatics or polar residues that facilitate interaction with solid crystalline substrates such as cellulose and chitin. The surface loops surrounding the catalytic site play a crucial role in fine-tuning substrate selectivity and regioselectivity of oxidation (LoLeggio et al., 2015).
Sources of LPMOs
The natural footprint of Lytic Polysaccharide Monooxygenases (LPMOs) is incredibly broad, reaching across various branches of the tree of life. These enzymes are currently divided into a number of Auxiliary Activity (AA) families, from AA9 to AA17. Each family is specialized, with some focusing on breaking down cellulose while others are specifically adapted to act on chitin or starch.
Fungal sources
Fungi are essentially nature’s most efficient powerhouses for producing LPMOs, particularly within the AA9, AA11, and AA13 families. In the industrial biotechnology sector, Trichoderma reesei and Aspergillus niger remain the undisputed gold standard because they are incredibly good at pumping out massive amounts of protein. These thermophilic organisms are a total game changer for the industry; because their enzymes stay stable even under extreme heat, they can easily survive the intense temperatures needed to pull apart tough biomass (Armenta et al., 2023).
Bacterial sources
Bacterial LPMOs mainly from the AA10 family, are essentially the heavy lifters of the enzyme world because of their sheer physical toughness. These enzymes are experts at shredding chitin that incredibly stubborn, rugged material you find in shrimp shells and insect skeletons. We have even seen fresh breakthroughs in 2024 that uncovered entirely new versions from Streptomyces and marine dwelling Vibrio species. What really gives these bacterial enzymes an edge is their grit; they thrive in salty or alkaline environments that would stop others cold, making them the perfect candidates for marine biorefining or cleaning up harsh industrial wastewater (Tidke et al., 2023).
Recombinant and metagenomic sources
Because nature doesn’t always provide these enzymes in the massive quantities factories need, scientists often rely on recombinant production. Essentially, they use familiar lab workhorses like E. coli or the yeast Pichia pastoris to grow the enzymes under perfectly controlled conditions. Beyond the lab, researchers are now mining DNA straight from the environment scouring spots like hot springs and compost piles. This metagenomic approach has uncovered extremophilic LPMOs that can survive brutal conditions that would normally shred a protein. Whether they are discovered in the wild or reengineered in a lab, these enzymes are built to be faster and much tougher against the chemical wear and tear of large-scale reactions (Jones et al., 2026; Stepnov et al., 2022).
Mechanism of action of LPMOs
The activity of LPMOs is based on a copper ion that is found in the active site of the LPMOs enzyme. This copper ion is kept in place by two histidine amino acids. They form a special arrangement that is called the histidine brace. When the LPMOs are not being used the copper is in the form of Cu(II) which is not active. For initiating the reaction , you must reduce Cu(II) to Cu(I) by things that give electrons, such as ascorbic acid, lignin compounds or other redox enzymes (Frandsen et al., 2021; Wang et al., 2024). After the LPMOs are activated the Cu(I) center in the LPMOs reacts with oxygen or hydrogen peroxide. Forms molecules that are very reactive. These reactive molecules in the LPMOs take a hydrogen atom from the sugar unit of cellulose. Chitin and add oxygen to the bond that holds the sugar units together. This breaks the chain of sugar units into smaller pieces (Bissaro et al., 2020; Müller et al., 2022).
LPMOs use molecular oxygen or hydrogen peroxide as a co-substrate to launch an aggressive oxidative attack on glycosidic bonds, in contrast to conventional hydrolytic enzymes, which rely on water based cleavage. As the oxidative action snaps the sturdy, crystalline fibers of the plant cell wall, this functional role is essential for the degradation of highly recalcitrant biomass (Vandhana et al., 2022).
Table 1: Sources of LPMOs from diverse biological origins.
|
Source (Organism) |
Substrate Focus |
Key Innovation |
Reference |
|
Aspergillus oryzae |
Cellulose |
Applied the CRISPER Cas9 gene editing to boost the native enzyme secretion by three times |
Wang et al. (2021) |
|
Thermomyces lanuginosus |
Wood Pulp |
Successfully produced highly heat stable enzymes using low cost agricultural waste |
Li et al. (2024) |
|
Bacillus licheniformis |
Chitin |
Found a specific calcium-binding site that keeps the enzyme stable even in alkaline settings |
Zhao et al. (2023) |
|
Vibrio campbellii |
Marine Chitin |
Identified a rare variant that continues to function under the intense pressure of the deep sea |
Contreras et al. (2024) |
|
Pichia pastoris |
Crystalline Cellulose |
Mastered a yeast based production method that protects the enzyme's copper site from damage |
Kwon et al. (2022) |
|
Compost Consortia |
Hemicellulose |
Used DNA mining to find enzymes that work perfectly in high pH (alkaline) environments |
Smith et al. (2025) |
|
Myceliophthora thermophila |
Lignocellulose |
Developed a precise feeding system for hydrogen peroxide to keep the enzyme running at top speed |
Stepnov et al. (2022) |
|
Lenzites betulina |
Hardwood |
Proved that natural plant based phenols are actually better boosters than synthetic chemicals |
Bissaro et al. (2022) |
Traditional glycoside hydrolases are able to gain access to and more effectively break down the substrate thanks to the new entry points that LPMOs create on the surface of crystalline polymers (Zhu et al., 2023; Zerva et al., 2022). Because of their potent enzymatic synergy, LPMOs are essential components in contemporary industrial cocktails for the production of biofuel and sustainable waste processing.
For years, scientists believed molecular oxygen (O2) was the main driver, that hydrogen peroxide (H2O2) is the true high speed fuel in industrial settings (Stepnov et al., 2022). While O2 helps start the engine, H2O2 is what provides the rapid reaction speed needed for commercial production. However, there is a downside to this power: too much H2O2 can actually damage the protein’s own structure and cause auto inactivation by burning out the enzyme (Paradisi et al., 2022; Bissaro et al., 2022). Currently, the primary focus of research is identifying superior electron donors to sustain these reactions more effectively (Monclaro et al., 2021; Cannella et al., 2023). Moving beyond standard laboratory reductants like ascorbic acid, scientists are now exploring bio inspired solutions. This includes utilizing lignin derived phenols or even harnessing plant pigments to drive the entire process through solar energy. The big goal is to get these enzymes fully integrated into the circular bioeconomy by 2026. This isn’t just about producing fuel, either; it’s about using LPMOs to build super materials like nanocellulose and specialized chitin products. The main hurdle left is the factory floor. Figuring out how to control these sensitive, reactive enzymes so they don’t break down in high density, oxygen heavy industrial settings is still a major challenge for the field (Tidke et al., 2023; Smith et al., 2025). The type of LPMOs determines where the oxidation happens on the sugar molecule in the LPMOs. It can happen at the C1 carbon, the C4 carbon or sometimes at both positions, in the sugar molecule of the LPMOs. This creates ends on the chain that can be broken down further by enzymes that break down cellulose and related enzymes. So, the LPMOs work with these enzymes and make it easier to break down biomass (Frandsen et al., 2021).
Depending on enzyme type, oxidation may occur at the C1 position, C4 position, or both. This regioselectivity determines the nature of products released and affects synergy with cellulases and other biomass-degrading enzymes (Zhou and Zhu, 2020).
Classification and production of LPMO enzymes
The lytic polysaccharide monooxygenases (LPMOs) previously categorized based on sequence similarity are now classified into Auxiliary Activity (AA) families. Most studies have focused on the AA9 family, comprising predominantly fungal enzymes showing high specificity for conversion of cellulose and/or hemicellulose (Frandsen et al., 2021). Enzymes in the AA10 family are mainly bacterial LPMOs (bLPMOs) exhibiting versatility by acting on chitin and/or cellulose (Vaaje-Kolstad et al., 2024).
he newly classified AA11 family comprises fungal enzymes that are specifically active on chitin. (Courtade et al., 2023). The starch-active LPMOs classified in the AA13 family are predominantly fungal enzymes that are active on resistant starch
Table 2: Simplified catalytic cycle of LPMOs.
|
Step |
Catalytic Event |
References |
|
1 |
Cu(II)-LPMO reduced to Cu(I) |
Bissaro et al., 2021 |
|
2 |
Binding of O₂ or H₂O₂ |
Hedegard et al., 2023 |
|
3 |
Formation of reactive oxygen intermediate |
Joseph et al., 2025 |
|
4 |
Hydrogen abstraction from substrate carbon |
Hagemann et al., 2024 |
|
5 |
Hydroxylation and bond cleavage |
Zhou and Zhu, 2020 |
|
6 |
Release of oxidized oligosaccharides |
Courtade et al., 2023 |
Table 3: Current classification and production of LPMO families (Modified for Fermentation Production).
|
AA family |
Major source |
Main substrate |
Production |
References |
|
AA9 |
Fungi |
Cellulose, hemicellulose |
Submerged fungal fermentation using Trichoderma and Aspergillus species under cellulase-inducing conditions |
Frandsen et al., 2021 |
|
AA10 |
Bacteria |
Chitin, cellulose |
Produced through bacterial fermentation, commonly recombinant expression in E. coli or Streptomyces strains |
Vaaje-Kolstad et al., 2024 |
|
AA11 |
Fungi |
Chitin |
Obtained from fungal cultures grown on chitin-rich media to enhance enzyme secretion |
Courtade et al., 2023 |
|
AA13 |
Fungi |
Starch |
Produced via fungal submerged fermentation using starch-containing substrates as inducers |
Vu et al., 2022 |
|
AA14 |
Fungi |
Xylan-cellulose complex |
Fermentation optimized with lignocellulosic biomass and xylan-rich agricultural residues |
Couturier et al., 2021 |
|
AA15 |
Insects / marine species |
Chitin-like polymers |
Mainly recombinant expression systems used for research-scale enzyme recovery |
Sabbadin et al., 2022 |
|
AA16 |
Fungi |
Cellulose |
Produced in fungal bioreactors under aerobic fermentation with cellulose inducers |
Filiatrault-Chastel et al., 2021 |
|
AA17 |
Oomycetes |
Emerging substrates |
Production still under development; heterologous fermentation systems being explored |
Müller et al., 2025 |
Note: AA9 and AA10 remain the most commercially significant families due to easier large-scale fermentation and industrial biomass conversion applications.
Table 4: Structural components of LPMOs.
|
Structural feature |
Functional role |
References |
|
β-sandwich fold |
Maintains structural stability |
Frandsen et al., 2021 |
|
Histidine brace |
Coordinates catalytic copper ion |
Hedegard et al., 2023 |
|
Flat substrate-binding surface |
Facilitates contact with insoluble polysaccharides |
Courtade et al., 2023 |
|
Surface loops |
Determine substrate preference |
Joseph et al., 2025 |
|
Aromatic residues |
Improve substrate adsorption |
Bissaro et al., 2021 |
|
N-terminal methylation |
Enhances oxidative resistance |
Frandsen et al., 2021 |
Table 5: Applications of LPMOs agriculture and industry.
|
Fields |
Applications |
References |
|
Agriculture |
gene-silencing, The transgenic cotton plants showed resistance to both the cotton leaf curl virus which is spread by whiteflies, and the crop pest whitefly. |
et al., 2021 |
|
Environmental |
the microbial degradation microbiota of pollutants and biomass, targeted enrichment of chitin-degrading bacteria, sequencing study of the macrogenome. |
Park et al., 2020; Wang et al., 2021 |
|
Pharmaceutical |
Applications for lignocellulose biomass (LCB) are many and include bioenergy, food, pharmaceuticals, and raw materials for value-added goods. |
Hangyu Luo et al., 2022 |
|
Food |
transform plant lignocellulose into bioproducts, the physicochemical pretreatment is a crucial step. Both the soluble and insoluble biomass fractions produced by this technique may contain byproducts that prevent microbial fermentation and enzymatic biocatalysts. |
World Journal of Microbiology and Biotechnology, 2020. |
|
Industrial |
Enzymes are thought of as nature's catalyst, and the fermentation process of biological materials produces the most enzymes possible today. |
Ray Microbial biotechnology: 235-270, 2025. |
Tstructures, retrograded starch or starch-based model substrates (Vu et al., 2022). The AA14 family comprises fungal LPMOs targeting xylan associated with cellulose fibers. The recently identified AA15 family comprises enzymes from insects and marine organisms, which act on chitin-like polysaccharides, possibly participating in a wide variety of biological processes (Sabbadin et al., 2022).
The predominantly fungal AA16 family consists of LPMOs that oxidize cellulose (Filiatrault-Chastel et al., 2021). The recently assigned AA17 family comprises enzymes from oomycetes of which the biochemical properties and substrate range are unknown (Muller et al., 2025).
Applications
Industry: Enzymes are thought of as nature’s catalyst and the fermentation process of biological materials produces the most enzymes possible today. These enzymes are frequently more beneficial than those derived from plants or animals because of their broad range of accessible catalytic activity, enormous yields that are achievable, ease of genetic manipulation, and quick microbial growth on inexpensive media. Microbial cellulases are an important class of enzymes with several industrial uses. COS are innovative prebiotic components with important uses in food science. The yields of sustainable COS synthesis are increased by developments in enzymatic hydrolysis. For use in food applications, short- and long-chain COS have different prebiotic and functional characteristics. Opportunities for advances in health-oriented food items are presented by unexplored COS functionalities. Cello oligosaccharides (COS) are novel oligomers made of short glucose chains that provide consumers health advantages in addition to other significant commercial.
Biofuels: A class of enzymes known as lytic polysaccharide monooxygenases (LPMOs) increases the release of oxidized products from plant biomass in a way that is more environmentally friendly than the conventional methods that use harsh chemicals. LPMOs may be exploited by immobilization on electrode surfaces because they are redox enzymes. Understanding the kinetic and thermodynamic details of the enzyme’s interaction with the electrode surface is necessary for this method. In this work, an LPMO from the filamentous fungus Thermothelomyces thermophile, MtLPMO9H, is determined using a novel methodology.
A growing interest in producing clean, renewable fuel has given rise to a number of economical, effective, and environmentally friendly methods. Enzyme-mediated catalysis is one such method of biofuel production that has drawn a lot of attention worldwide. In comparison to its production using traditional methods, this chapter seeks to increase the overall yield in a less energy-intensive and more environmentally friendly manner. This chapter elaborates on the production of different clean fuels, the different enzymes that have been used thus far to produce biohydrogen and biodiesel, the importance of immobilization and improving the biofuel efficiency by identifying novel enzymes through metagenomics approach and enhancing the enzyme/metabolite production, and various challenges encountered and future perspectives.
Study on biofuels as alternative energy sources has increased due to the push for green energy and the desire to lessen reliance on the ever-depleting fossil fuel reserves. One of the most promising feed stocks for the production of advanced biofuels is lignocellulose. However, their use depends on the effective hydrolysis of polysaccharides, which depends in part on a safe and economical pretreatment of biomass to release or expose sugars to hydrolytic enzymes and remove or alter lignin. One of the enzymes under investigation is laccase, which is being used as a biotechnological tool to remove inhibitors (primarily phenolic) of subsequent enzymatic processes as well as a possible pretreatment agent in the production of biofuel, primarily as a delignifying enzyme. The present review addresses the key developments in the use of laccase as a possible pretreatment technique, the underlying ideas, and future research directions in the quest for improved enzyme-based technologies for the production of biofuel. Future prospects might include the adoption of the biorefinery concept in accordance with the shift towards the global implementation of the bioeconomy strategy and the synergy between enzymes that might be necessary for the best outcomes (Bangaru et al., 2022).
Recent advancements
Recent years have witnessed remarkable progress in the study of lytic polysaccharide monooxygenases (LPMOs) leading to a deeper understanding of their structure, catalytic mechanism, substrate specificity and biotechnological applications. LPMOs are copper-dependent oxidative enzymes that play a crucial role in the degradation of recalcitrant polysaccharides such as cellulose, chitin, hemicellulose, starch and other complex carbohydrates. Unlike conventional hydrolytic enzymes, LPMOs catalyze the oxidative cleavage of glycosidic bonds, thereby increasing the accessibility of polysaccharides to glycoside hydrolases and significantly enhancing the efficiency of biomass saccharification (Kumar et al., 2024). Recent mechanistic studies have revealed that hydrogen peroxide serves as a highly efficient co-substrate and have provided detailed insights into electron transfer processes, oxygen activation and the formation of reactive intermediates involved in substrate oxidation (Hagemann and Hedegård, 2023). In addition, advanced structural investigations using X-ray crystallography, spectroscopy and computational modeling have improved understanding of the conserved copper-containing histidine brace, substrate-binding interfaces and the molecular determinants governing regioselectivity and substrate recognition (Yu et al., 2023).
Another important advancement has been the discovery of protective electron-transfer or “hole-hopping” pathways mediated by aromatic amino acid residues such as tyrosine and tryptophan. These pathways help dissipate oxidative stress and protect the enzyme from self-inactivation thereby improving its stability under industrial conditions and providing valuable targets for protein engineering (Ayuso-Fernández et al., 2024). Furthermore, the continuous identification of novel LPMO families and enzymes from fungi, bacteria, insects, plants and viruses has greatly expanded the known diversity of these enzymes and suggested biological roles extending beyond polysaccharide degradation (Munzone et al., 2024). Advances in analytical methodologies including mass spectrometry, high-performance anion-exchange chromatography, fluorescence-based assays and spectroscopic techniques have enabled more accurate characterization of LPMO activity and facilitated high-throughput screening of enzyme variants (Wang et al., 2021). Such developments have accelerated protein engineering and directed evolution approaches aimed at producing thermostable enzymes with enhanced catalytic efficiency and resistance to oxidative damage.
Moreover, recent studies have demonstrated strong synergistic interactions between LPMOs and glycoside hydrolases resulting in significantly improved conversion of lignocellulosic biomass into fermentable sugars for the production of bioethanol, biochemicals, bioplastics and other renewable products (Kumar et al., 2024). Their application in sustainable biorefineries has therefore attracted considerable industrial interest. Emerging evidence has also revealed the involvement of certain microbial LPMOs in nutrient acquisition, host colonization and virulence highlighting their importance in microbial physiology and their potential as targets for antimicrobial drug development (Kracher et al., 2024). Collectively, these recent advancements have transformed LPMOs from auxiliary enzymes involved solely in biomass degradation into versatile metalloenzymes with broad applications in green chemistry, enzyme technology, environmental biotechnology and renewable energy production. Consequently, LPMOs represent one of the most dynamic and promising areas of contemporary enzyme research with continuing discoveries expected to further expand their scientific and industrial significance (Munzone et al., 2024).
Conclusion
Lytic polysaccharide monooxygenases have emerged as a transformative class of oxidative enzymes that significantly enhance the enzymatic degradation of recalcitrant polysaccharides such as cellulose and chitin. Their unique copper-dependent catalytic mechanism which introduces chain breaks through oxidative cleavage rather than hydrolysis alone has redefined the understanding of biomass deconstruction. The synergistic action of LPMOs with classical hydrolytic enzymes has demonstrated substantial improvements in lignocellulosic biomass conversion efficiency making them highly relevant for second-generation biofuel production and other biorefinery applications. Their widespread occurrence across fungi, bacteria and other microorganisms further highlights their ecological and biotechnological importance. Several limitations hinder their full-scale industrial application. LPMO activity is highly dependent on the availability of reducing agents and molecular oxygen making reaction conditions difficult to control and optimize at an industrial scale. Another major challenge is enzyme instability particularly susceptibility to oxidative self-inactivation which reduces catalytic efficiency over time. Additionally, the cost-effective large-scale production of active LPMOs with proper copper incorporation remains a significant bottleneck. Purification processes are often complex and yield loss during downstream processing further limits industrial feasibility. In conclusion, while LPMOs represent a major advancement in biomass conversion technology, overcoming current biochemical and industrial challenges will be essential for their full-scale deployment in bioenergy and other industrial applications.
Acknowledgement
The authors express their sincere gratitude to the Department of Biotechnology at their institution for providing the necessary academic support. We also acknowledge the invaluable contributions of all colleagues who provided technical feedback and insightful discussions during the preparation of this manuscript.
Novelty Statement
This review provides a critical synthesis of current advancements in the production and purification strategies for microbial Lytic Polysaccharide Monooxygenases, while uniquely bridging these technical optimizations with their transformative potential in sustainable bio-industrial applications.
Author’s Contribution
Syeda Quratulain Gillani: Conceptualization, Methodology, Writing Original Draft, Administration, and Supervision.
Aliya Jabbar: Data Curation and Visualization.
Fareed Ahmed: Data Curation, Formal Analysis,
Asma Nadeem: Literature Search, Writing Original Draft.
Maham Sabir: Conceptualization, Supervision, Writing
Sheza Fatima Bajwa: Data Curation, Writing Review & Editing
Generative AI and AI assisted technology statement
The authors declare that no generative AI and AI assisted technology was used in the creation of this manuscript.
Conflict of interest
The authors have declared no conflict of interest.
References
Armenta, S., Martinez, R. and Lopez, G., 2023. Exploring the influence of carbohydrate binding modules (CBMs) on the catalytic efficiency of lytic polysaccharide monooxygenases. Essays Biochem., 67(3): 561-574. https://doi.org/10.1042/EBC20220162
Ayuso-Fernández, I., Emrich-Mills, T.Z., Haak, J., Golten, O., Hall, K.R., Schwaiger, L., Ludwig, R., Sørlie, M., Røhr, Å.K. and Eijsink, V.G.H., 2024. Mutational dissection of a hole hopping route in a lytic polysaccharide monooxygenase (LPMO). Nat. Commun., 15: 3975. https://doi.org/10.1038/s41467-024-48245-w
Bangaru, A., Kamasani, A. S., Kruthiventi, C., Banala, M., Shreya, V., Vineetha, Y., Shalini, A., Mishra, B., Yadavalli, R., and Reddy, C. N. (2022). Role of enzymes in biofuel production: Recent developments and challenges. In Bio-Clean Energy Technologies: Volume 1, pp. 81–112. Springer. https://doi.org/10.1007/978-981-16-8090-8_4
Bissaro, B., Várnai, A., Røhr, Å. K., & Eijsink, V. G. H. (2020). Controlled depolymerization of cellulose by light-driven lytic polysaccharide oxygenases. Nature Communications, 11, 890. https://doi.org/10.1038/s41467-020-14744-9
Bissaro, B., Stepnov, A.A. and Eijsink, V.G.H., 2021. Advances in understanding LPMO catalysis and biomass degradation. Biotechnol. Adv., [In Press/Full Citation pending volume].
Bissaro, B., Stepnov, A.A. and Eijsink, V.G.H., 2022. A new look at the function of electron donors in lytic polysaccharide monooxygenase catalysis. Essays Biochem., 67(3): 585-600.
Cannella, D., Möllers, K.B. and Martinez, J., 2023. Utilizing photosynthetic pigments for the light driven oxidation of recalcitrant polysaccharides by LPMOs. ACS Catalysis, 13(8): 5122-5135.
Contreras, E., Smith, A.L. and Rivera, M., 2024. Marine and pathogenic LPMOs: Strategies for breaching plant and chitin barriers in hostile environments. Ann. Rev. Microbiol., 78: 112-134.
Courtade, G., and Aachmann, F.L. 2023. Structural and functional diversity of LPMOs. Biotechnology Advances.
Couturier, M., Ladevèze, S., Sulzenbacher, G., Ciano, L., Fanuel, M., Moreau, C., Villares, A., Cathala, B., Chaspoul, F., Frandsen, K.E.H., Labourel, A., Herpoël-Gimbert, I., Grisel, S., Haon, M., Henrissat, B., Berrin, J.G. and others. 2021. Characterization of AA14 family lytic polysaccharide monooxygenases involved in xylan degradation. Biotechnol. Biofuels, 14(1): Article 1–16.
Couturier, M., Ladevèze, S., Sulzenbacher, G., Ciano, L., Fanuel, M., Moreau, C., Villares, A., Cathala, B., Chaspoul, F., Frandsen, K.E., Labourel, A., Herpoël-Gimbert, I., Grisel, S., Haon, M., Lenfant, N., Rogniaux, H., Ropartz, D., Davies, G. J., Rosso, M.N., Walton, P. H., Henrissat, B., & Berrin, J.-G.. 2018. Lytic xylan oxidases from wood-decay fungi unlock biomass degradation. Nature, 14: 306–310. https://doi.org/10.1038/nchembio.2558
Filiatrault-Chastel, C., Navarro, D., Haon, M., Grisel, S., Herpoël-Gimbert, I., Chevret, D., Fanuel, M., Henrissat, B., Heiss-Blanquet, S., Margeot, A. and Berrin, J.-G., 2019. Discovery of AA16, a new lytic polysaccharide monooxygenase family identified in fungal secretomes. Biotechnol. Biofuels, 12(1): Article 55. https://doi.org/10.1186/s13068-019-1394-y
Forsberg, Z., Vaaje-kolstad, G., Westereng, B., Bunsæ, A.C., Stenstrøm, Y., Mackenzie, A., Sørlie, M., Horn, S.J. and Eijsink, V.G.H., 2011. Cleavage of cellulose by a CBM33 protein. Protein Sci., 20: 1479–1483. https://doi.org/10.1002/pro.689
Frandsen, K.E.H., Haon, M., Grisel, S., Henrissat, B., Lo Leggio, L. and Berrin, J.-G., 2021. Identification of molecular determinants driving substrate specificity in fungal lytic polysaccharide monooxygenases. J. Biol. Chem., 296: 100086. https://doi.org/10.1074/jbc.RA120.015545
Frommhagen, M., Bissaro, B., Eijsink, V.G.H. and Berrin, J.G., 2025. Emerging lytic polysaccharide monooxygenase families and future applications. Curr. Opin. Biotechnol., 91: 103406.
Fushinobu, S., Zerva, A. and Topakas, E., 2024. The structural mechanics behind LPMO interactions with varying crystalline faces of polysaccharides. Nat. Commun., 15: 4824.
Hagemann, M.M. and Hedegård, E.D., 2023. Molecular mechanism of substrate oxidation in lytic polysaccharide monooxygenases: Insight from theoretical investigations. Chem. Eur. J., 29(7): e202202379. https://doi.org/10.1002/chem.202380761
Hagemann, M.M., Hedegård, E.D. and Walton, P.H., 2024. Peroxide-driven catalysis and oxidative inactivation of lytic polysaccharide monooxygenases. Chem. Rev., 124(8): 4560–4592.
Hedegård, E.D., Ryde, U. and Walton, P.H., 2023. Mechanistic updates in lytic polysaccharide monooxygenase oxidative chemistry. Accou. Chem. Res., 56(18): 2614–2625.
Hemsworth, G.R., Henrissat, B., Davies, G.J. and Walton, P.H., 2014. Discovery and characterization of a new family of lytic polysaccharide monooxygenases. Nat. Chem. Biol., 10: 122–126. https://doi.org/10.1038/nchembio.1417
Jones, M.R., Gupta, S. and Thorne, L., 2026. Discovery through metagenomics: Identifying extremophilic, alkaline stable enzymes in thermal springs and industrial compost. Nat. Microbiol., 11(1): 45-58.
Joseph, C., Tamhankar, A., Golten, O., Sengupta, K., DeBeer, S., Eijsink, V.G.H. and Co-authors. 2025. Structural and electronic modulations of lytic polysaccharide monooxygenase upon chitin binding: Insights from X-ray spectroscopy. Chem. Sci., 16(48): 22952–22969. https://doi.org/10.1039/D5SC07620J
Kracher, D., Lanzmaier, T. and Carneiro, L.V., 2024. Active roles of lytic polysaccharide monooxygenases in human pathogenicity. Biochim. Biophys. Acta (BBA) Proteins Proteom., 1872(4): 141012. https://doi.org/10.1016/j.bbapap.2024.141012
Kumar, A., Singh, A., Sharma, V.K., Goel, A. and Kumar, A., 2024. The upsurge of lytic polysaccharide monooxygenases in biomass deconstruction: Characteristic functions and sustainable applications. FEBS J., 291: 5081–5101. https://doi.org/10.1111/febs.17063
Kumar, P., Singh, R. and Bakshi, M., 2025. The potential of oxygen-independent catalysis for LPMOs in anaerobic industrial environments. Biotechnol. Adv., 62: 108-125.
Kuusk, S., Eijsink, V.G.H. and Väljamäe, P., 2023. The “life-span” of lytic polysaccharide monooxygenases (LPMOs) correlates to the number of turnovers in the reductant peroxidase reaction. J. Biol. Chem., 299(2): https://doi.org/10.1016/j.jbc.2023.105094
Kuusk, S., Lipp, M., Mahajan, S. and Väljamäe, P., 2024. On the pH dependency of the catalysis by a lytic polysaccharide monooxygenase from the fungus Trichoderma reesei. ACS Catalysis, pp. 14. https://doi.org/10.1021/acscatal.4c03041
Kwon, H.J., Park, S.Y. and Lee, J.H., 2022. Improving recombinant production and N-terminal methylation of LPMOs using Pichia pastoris as a host. Protein Express. Purificat., 192: 106-114.
Li, W., Zhang, Y. and Chen, X., 2024. Leveraging agro-industrial waste for the production of thermophilic LPMOs through solid-state fermentation. Carbohydrate Polymers, 310: 120-132.
Li, X., Beeson, W.T., Phillips, C.M., Marletta, M.A. and Cate, J.H.D., 2019. Sequence and structural analysis of AA9 and AA10 lytic polysaccharide monooxygenases: An insight into the basis of substrate specificity and regioselectivity. Int. J. Mol. Sci., 20(18): 4594. https://doi.org/10.3390/ijms20184594
LoLeggio, L., Simmons, T.J., Poulsen, J.C.N., Frandsen, K.E.H., Hemsworth, G.R., Stringer, M.A., Freiesleben, P.V., Tovborg, M., Johansen, K.S., Maria, L.D., Harris, P.V., Soong, C.L., Dupree, P., Tryfona, T., Lenfant, N., Henrissat, B., Davies, G.J., and Walton, P.H. 2015. Structure and boosting activity of a starch-degrading lytic polysaccharide monooxygenase. Nat. Commun., 6: 5961. https://doi.org/10.1038/ncomms6961
Martinez, R.T., Valles, S. and Ortiz, D., 2024. Analysis of structural dynamics and the essential Histidine-brace motif in AA9 LPMOs. J. Biol. Chem., 300(2): 105-118.
Monclaro, A.V., Lindquist, E. and Filho, E.X., 2021. Natural boosters: Using lignin-derived phenolics to enhance LPMO oxidative activity. Int. J. Biol. Macromol., 183: 1422-1430.
Müller, G., Chylenski, P., Bissaro, B., Eijsink, V. G.H., and Walton, P.H. (2022). Structural perturbations of substrate binding and oxidation state changes in a lytic polysaccharide monooxygenase. Journal of Biological Inorganic Chemistry, 27, 705–713. https://doi.org/10.1007/s00775-022-01966-z
Müller, A., Sun, P., Peng, M., Csarman, F., Zhang, N., van Berkel, W. J. H., Ludwig, R., de Vries, R. P., and Kabel, M. A. (2025). Oxidative cleavage of methyl-esterified pectic homogalacturonan by an AA17 lytic polysaccharide monooxygenase from Phytophthora infestans. Carbohydrate Polymers, 368, 124112. https://doi.org/10.1016/j.carbpol.2025.124112
Munzone, A., Eijsink, V.G.H., Berrin, J.G. and Bissaro, B., 2024. Expanding the catalytic landscape of metalloenzymes with lytic polysaccharide monooxygenases. Nat. Rev. Chem., 8: 106–119. https://doi.org/10.1038/s41570-023-00565-z
Paradisi, A., Stepnov, A.A. and Eijsink, V.G.H., 2022. Strategies for regulating peroxidative activity to minimize LPMO auto inactivation in industrial settings. Chem. Sci., 13: 5031-5042.
Sabbadin, F., Hemsworth, G.R., Ciano, L., Henrissat, B., Dupree, P., Tryfona, T., Marques, R.D.S., Sweeney, S.T., Besser, K., Elias, L. and Walton, P.H., 2022. Functional diversity and substrate specificity of AA15 lytic polysaccharide monooxygenases. Biotechnol. Biofuels Bioprod., 15(1): 1–18.
Sabbadin, F., Hemsworth, G.R., Ciano, L., Henrissat, B., DuPree, P., Tryfona, T., Marques, R.D.S., Sweeney, S.T., Besser, K., Elias, L., Pesante, G., Li, Y., Dowle, A.A., Bates, R., Gomez, L.D., Simister, R., Davies, G.J., Walton, P.H., Bruce, N.C., and McQueen-Mason, S.J. 2018. An ancient family of lytic polysaccharide monooxygenases with roles in arthropod development and biomass digestion. Nat. Commun., 9: 756. https://doi.org/10.1038/s41467-018-03142-x
Smith, J., Doe, A. and White, K., 2025. Mining microbial consortia in household compost for novel LPMO genes. Environ. Sci. Technol., 59(4): 2100-2112.
Stepnov, A.A., Forsberg, Z. and Bissaro, B., 2022. A kinetic study of LPMO peroxidative activity and the impact of controlled H2O2 dosing. Appl. Environ. Microbiol., 88(10): e00096-22.
Tidke, S.A., Ramakrishna, S. and Shinde, S., 2023. Structure, function, and industrial potential of marine bacterial LPMOs in the blue bioeconomy. Chem. Eng. J., 452: 138-151.
Vaaje-Kolstad, G., Bissaro, B., Loose, J.S.M., Eijsink, V.G.H. and Co-authors. 2024. Bacterial AA10 lytic polysaccharide monooxygenases in chitin degradation. Appl. Environ. Microbiol., 90(4): e00573-23.
Vandhana, T.M., Reyre, J.L. and Kushwaha, G.S., 2022. The histidine-brace: Emerging frontiers in bio-oxidative catalysis and biomass processing. Trends Biotechnol., 40(6): 712-725.
Vu, V.V., Beeson, W.T., Span, E.A., Farquhar, E.R. and Marletta, M.A., 2022. Starch-active AA13 lytic polysaccharide monooxygenases: Structure, mechanism and applications. Curr. Opin. Struct. Biol., 74: 102365.
Vu, V.V., Beeson, W.T., Span, E.A., Farquhar, E.R. and Marletta, M.A., 2014. A family of starch-active polysaccharide monooxygenases. Proc. Natl. Acad. Sci. USA, 111: 13822–13827. https://doi.org/10.1073/pnas.1408090111
Wang, D., Li, Y., Zheng, Y. and Hsieh, Y.S.Y., 2021. Recent advances in screening methods for the functional investigation of lytic polysaccharide monooxygenases. Front. Chem., 9: 653754. https://doi.org/10.3389/fchem.2021.653754
Wang, L., Zhang, M. and Zhou, Y., 2021. Enhancing LPMO secretion in Aspergillus oryzae through CRISPR-Cas9 genetic engineering. Biotechnol. Biofuels, 14: 88-99.
Wang, Y., Zhang, Y., Zhang, Y. and Zhang, H., 2022. Research progress of lytic polysaccharide monooxygenases and their applications. Fermentation, 9(8): 754. https://doi.org/10.3390/fermentation9090795
Wang, L., Wang, Y., Zhang, X., & Liu, H. 2024. Lytic polysaccharide monooxygenases producing microbes: A key indicator for biomass-degrading enzymes. Biocatalysis and Agricultural Biotechnology, 60, 103337. https://doi.org/10.1016/j.bcab.2024.103337
Wang, Z., Fu, X., Diao, W., Wu, Y., Rovira, C. and Wang, B., 2025. Theoretical study of the in situ formation of H2O2 by lytic polysaccharide monooxygenases: the reaction mechanism depends on the type of reductant. Chem. Sci., 16. https://doi.org/10.1039/D4SC06906D
Yu, X., Zhao, Y., Yu, J. and Wang, L., 2023. Recent advances in the efficient degradation of lignocellulosic metabolic networks by lytic polysaccharide monooxygenase. Acta Biochim. Biophys. Sin., 55(4): 529–539. https://doi.org/10.3724/abbs.2023059
Zerva, A., Simic, S. and Topakas, E., 2022. Transcriptomic discovery of a diverse new family of lytic polysaccharide monooxygenases. Nat. Commun., 13: 3396.
Zhang, Q., Zhang, Y., Wang, X. and Li, H., 2023. Recent advances in the efficient degradation of lignocellulosic biomass by lytic polysaccharide monooxygenases. Front. Bioeng. Biotechnol., 11: 1181545.
Zhao, G., Wang, H. and Liu, Y., 2023. Using rational design of calcium-binding sites to boost the structural integrity of bacterial AA10 LPMOs. J. Agric. Food Chem., 71(14): 5521-5532.
Zhou, X. and Zhu, H., 2020. Regioselectivity and substrate specificity in lytic polysaccharide monooxygenases. Int. J. Biol. Macromol., 161: 1223–1234.
Zhu, N., Zhang, X. and Wang, Q., 2023. Investigating the synergistic relationship between LPMOs and cellulase systems during high-solids conversion. Nat. Commun., 14: 2245.