Next Article in Journal
Pineapple Waste Biorefinery: An Integrated System for Production of Biogas and Marketable Products in South Africa
Previous Article in Journal
Environmental Assessment of Tannin Extraction from Bark Residues for Application in Water Treatment
 
 
Font Type:
Arial Georgia Verdana
Font Size:
Aa Aa Aa
Line Spacing:
Column Width:
Background:
Review

High Impact Biomass Valorization for Second Generation Biorefineries in India: Recent Developments and Future Strategies for Sustainable Circular Economy

by
Ayisha Naziba Thaha
1,
Mehrdad Ghamari
2,
Gitanjali Jothiprakash
3,
Sasireka Velusamy
4,
Subburamu Karthikeyan
3,
Desikan Ramesh
1 and
Senthilarasu Sundaram
4,*
1
Department of Renewable Energy Engineering, Tamil Nadu Agricultural University, Coimbatore 641003, India
2
Cybersecurity and Systems Engineering, School of Computing, Engineering and the Built Environment, Edinburgh Napier University, Edinburgh EH10 5DT, UK
3
Centre for Post Harvest Technology, Agricultural Engineering College and Research Institute, Tamil Nadu Agricultural University, Coimbatore 641003, India
4
School of Computing, Engineering and Digital Technologies, Teesside University, Middlesbrough TS1 3JN, UK
*
Author to whom correspondence should be addressed.
Biomass 2025, 5(1), 16; https://doi.org/10.3390/biomass5010016
Submission received: 12 February 2025 / Revised: 7 March 2025 / Accepted: 13 March 2025 / Published: 18 March 2025

Abstract

:
India’s rapidly growing automobile industry has intensified the need for sustainable fuel alternatives to reduce dependency on imported fossil fuels and mitigate greenhouse gas (GHG) emissions. This study examines the potential of second-generation biorefineries as a comprehensive solution for efficient biomass valorization in India. With a projected bioethanol demand of 10,160 million liters by 2025 for India’s 20% ethanol blending target, there is an urgent need to develop sustainable production pathways. The biorefinery approach enables simultaneous production of multiple valuable products, including bioethanol, biochemicals, and bioproducts, from the same feedstock, thereby enhancing economic viability through additional revenue streams while minimizing waste. This paper systematically analyzes available biomass resources across India, evaluates integrated conversion technologies (biochemical, thermochemical, and synergistic approaches), and examines current policy frameworks supporting biorefinery implementation. Our findings reveal that second-generation biorefineries can significantly contribute to reducing GHG emissions by up to 2.7% of gross domestic product (GDP) by 2030 while creating rural employment opportunities and strengthening energy security. However, challenges in supply chain logistics, technological optimization, and policy harmonization continue to hinder large-scale commercialization. The paper concludes by proposing strategic interventions to overcome these barriers and accelerate the transition toward a sustainable circular bioeconomy in India.

1. Introduction

The global energy landscape is undergoing a profound transformation driven by environmental concerns, resource depletion, and the need for sustainable development. Fossil fuels, which have powered economic growth for decades, are now recognized as major contributors to climate change through greenhouse gas (GHG) emissions. This environmental impact, coupled with the finite nature of fossil fuel resources, has intensified the search for renewable alternatives that can meet growing energy demands while minimizing ecological footprints. In this context, biomass has emerged as a promising renewable resource with significant potential to address multiple challenges simultaneously. Unlike fossil fuels, which take millions of years to form, biomass is produced through photosynthesis in a relatively short timeframe, converting atmospheric CO2 into energy-rich organic compounds [1]. When these compounds are combusted, they release the stored energy and return CO2 to the atmosphere, creating a carbon-neutral cycle that significantly reduces net GHG emissions compared to fossil fuels. Biomass currently accounts for approximately 14% of global energy consumption, with developing nations utilizing 38% of this energy, particularly in rural areas where access to conventional energy sources remains limited [2]. India, with its favorable climate and extensive agricultural activities, possesses abundant biomass resources that present significant opportunities for sustainable energy production and utilization.
India’s vast agricultural landscape, spanning 1.78 million square kilometers [2], generates over 990 million metric tons of agricultural biomass annually [3]. This includes crop residues such as rice straw, wheat straw, sugarcane bagasse, and corn stover, which often remain unutilized or are burned in open fields, contributing to air pollution. Beyond agricultural residues, India’s biomass resources encompass municipal solid waste (approximately 160,000 tons daily) [4], forest residues from 71 million hectares of forested land [5], industrial byproducts [6], and aquatic biomass such as algae [7,8], which are increasingly recognized for their biofuel potential.
Traditional approaches to biomass utilization have focused primarily on single-product systems, such as dedicated bioethanol or biogas production facilities. However, these approaches often fail to maximize the value of biomass feedstocks and struggle with economic viability. The biorefinery concept addresses these limitations by enabling the simultaneous production of multiple products—including biofuels, biochemicals, and biomaterials—from the same raw materials [9]. This integrated approach enhances the economic sustainability of biofuel industries by generating additional revenue streams, minimizing waste, and facilitating more efficient resource utilization.
Valorization represents the critical process of converting biomass into valuable products through various conversion pathways [10]. Recent advancements in hydrothermal and biological treatments have significantly enhanced the efficiency of biomass valorization, enabling higher yields of desired products while minimizing environmental impacts [9,11]. These technologies are particularly relevant for second-generation biorefineries, which utilize non-food feedstocks such as agricultural residues, forestry waste, and dedicated energy crops [12], thereby avoiding the food-versus-fuel debates associated with first-generation biofuels. In the context of biomass feedstocks, various materials exhibit differing levels of productivity, contributing significantly to multiple industries. As detailed in the results section, microalgae (Nannochloropsis), used in biodiesel and renewable energy production, show an average productivity of 10.7 m3/ha/year, with the potential to reach up to 36.3 m3/ha/year [13]. Switchgrass, utilized for bioenergy and biofuels, has a productivity range of 5.1 to 8.6 Mg/ha/year [14]. Soybean residues, primarily used for biogas production, offer 384.5 m3/ha/year for biogas [15]. Woody biomass, including pine and eucalyptus, which serve various industries such as bioenergy, pulp and paper, and aviation fuels, can yield up to 115 Mg/ha over a 10-year period [16]. Corn stover and switchgrass, used for bioenergy in pelletized fuels, have unspecified productivity, but their energy density increases when blended [17]. Forest residues from logging, contributing to bioenergy and district heating, can generate up to 40 TWh/year between 2030 and 2050 [18]. These results highlight the varying productivity of biomass feedstocks, emphasizing their potential for large-scale utilization in renewable energy and bio-based product industries.
The implementation of second-generation biorefineries in India faces several challenges, including logistical issues in biomass collection and transportation, technological barriers in conversion processes, and policy frameworks that may not fully support integrated biorefinery approaches. Addressing these challenges requires a comprehensive understanding of available biomass resources, conversion technologies, and policy mechanisms that can foster sustainable biorefinery development.
This paper systematically analyzes second-generation biorefinery approaches for efficient biomass valorization in India. It assesses the availability and characteristics of various biomass feedstocks across different regions, evaluates biochemical, thermochemical, and synergistic technologies for biomass conversion, and examines policy frameworks and institutional mechanisms supporting biorefinery development. Additionally, it identifies challenges and proposes strategies to overcome barriers to commercial implementation while analyzing the potential environmental, economic, and energy impacts of widespread biorefinery adoption within a circular economy framework.

2. Biorefinery Technologies Involved in Biomass Valorization

Second-generation biorefineries mainly utilize non-food feedstock, namely crop residues, agro-processing waste, algae, aquatic plants, and energy crops with a focus on addressing the food security issues allied with first-generation biorefineries [12]. It produces biofuels, bio-products, and biochemicals in an efficient manner [9]. The technologies involved in second-generation biorefineries are biochemical and thermochemical conversion technology (Figure 1) and synergistic approaches for effectively utilizing the resource in a sustainable way.

2.1. Biochemical Conversion Technology

Biochemical conversion technologies emphasize exploiting biological processes such as fermentation and anaerobic digestion for biomass valorization [19]. The fermentation of pretreated biomass results in the production of biohydrogen, bioethanol, biobutanol, organic acids, biopolymers, and biochemicals upon down-streaming [20]. Anaerobic digestion converts biomass into biogas and bio-digestate. Biogas is a mixture of methane, carbon dioxide, traces of H2S, and water vapor. This can be purified via steam reforming or the pressure swing method to synthesize biomethane, biohydrogen, and carbon dioxide for commercial applications. The bio-digestate can be used a solid or liquid bio-manure for agriculture as it a good soil amendment material [21]. These technologies are an integral part of second generation biorefineries, allowing them to produce liquid biofuels (bioethanol, biobutanol), organic acids, biochemicals, and biohydrogen, even though they require costly pretreatment operations. The biogas production from biomass is a highly suitable and eco-friendly technology. Pretreatment of wet biomass can be ignored, and high fibrous material requires rigorous pretreatment for the effective digestion of the materials. Bioethanol and biogas production from biological processing is a proven technology in second-generation biorefineries [22].

2.2. Thermochemical Conversion Technology

Thermochemical conversion technology utilizes heat, resulting in chemical reactions of biomass to convert into bioenergy, biofuels, and bioproducts. Combustion, pyrolysis, and gasification are the basic thermo-chemical conversion technologies [23]. Hydrothermal Carbonization (HTC) and hydrothermal Liquefaction (HTL) fall under the label of advanced technologies. Pyrolysis is an anaerobic process that converts biomass into bio-oil, biochar, and pyrogas (Syngas) in the presence of heat. The biochar is used for bioenergy, soil amendment, and as an adsorbent. Bio-oil is used as a biofuel and bio-lubricant in industry [24]. In the gasification process, biomass is partially oxidized to synthesize syngas. Syngas is a mixture of carbon monoxide, carbon dioxide, hydrogen, and hydrocarbons, which can be streamed to produce biohydrogen, liquid fuels, etc. [25]. HTC converts wet biomass into a carbon-dense solid material called hydrochar, along with an aqueous phase and biocrude, under subcritical water conditions. It operates under high pressure and moderate temperature in the range of 2–10 MPa and 180–250 °C, respectively. Subcritical water is liquid water under high temperature and pressure, above normal boiling conditions but below its critical point (T: 100–374.2 °C and P: 0.1–22.1 MPa) [26]. HTL converts wet biomass into a liquid material called biocrude, along with hydrochar and an aqueous phase, under subcritical and supercritical water conditions. This process involves high pressure (10–25 MPa) and high temperature (250–400 °C). Supercritical water is obtained when water exceeds its critical point (Tc: 374.2 °C and Pc: 22.1 MPa). HTC is carried out under subcritical water conditions, while HTL operates under subcritical conditions and can reach supercritical water conditions [27]. The biocrude can be refined to produce petrol, diesel, kerosene, alkenes, phenols, acids, and carbon dots. The hydro-char can be utilized as an electrode, as an adsorbent, and as bio-coal. The aqueous phase can be utilized as a bio-fertilizer, as it contains more nutrients, to grow algae, to recover chemicals, or as a soil amendment material. In general, thermochemical conversion technologies provide litheness in utilizing heterogenous kinds of biomass with higher conversion efficiency [28]. Table 1 details the use of several primary and secondary feedstocks through various biorefinery technologies to yield bioproducts and co-products.
Table 1. Biorefinery Technologies for Biomass Utilization and Value Addition.
Table 1. Biorefinery Technologies for Biomass Utilization and Value Addition.
Primary FeedstockSecondary FeedstockTechnologyProductsCo-ProductsReference
Corn StoverFood waste, crop residuesFermentationBioethanol, Bio-based chemicalsCO2, Furfural, Lignin[29,30,31,32]
Sugarcane BagasseRice husk, coconut shellFermentationBioethanol, BiobutanolLignin, Xylitol, Acetic acid[1,33,34]
Paddy StrawWheat straw, maize stalksFermentationBioethanol, BiomethaneLignin, Animal Feed[35,36]
Poplar Willow, EucalyptusFermentationBioethanol, Acetic acidLignin, Biochar[37,38,39]
Cocoa PodsCoffee husks, banana stemsFermentationBiochemical, Organic acidsLiquor[40,41]
Food Waste Kitchen wasteFermentation, Anaerobic DigestionBioethanol, organic acidsBiogas, Organic Fertilizer[42,43,44]
Coconut ShellKernel shells, paddy huskPyrolysisBiochar, Bio-oil, Activated carbonPyrogas[45]
Water HyacinthDuckweed, algaePyrolysisBio-oil, BiocharPyrogas, Bio-fertilizer[46,47,48]
WillowMiscanthus, PoplarPyrolysis, gasificationSyngas, Biochar, Bio-oilHeat, Power[49,50,51,52]
WoodAgricultural residues, sawdust, barkPyrolysis, GasificationBio-oil, Biochar, SyngasBiochar, Heat, Power[53,54,55,56]
SwitchgrassWood chips, wheat strawPyrolysis, GasificationBio-oil, SyngasBiochar, Electricity[57,58,59,60,61,62]
MicroalgaeSeaweed, wastewaterAlgae-based BiorefineryBiodiesel, BioethanolAnimal Feed, Biochar[63,64,65,66]

2.3. Synergistic Approach

Second-generation biorefineries gradually explore synergistic approaches that integrate both biochemical and thermochemical conversion technologies to valorize biomass effectively. For example, bio-digestate from anaerobic digestion can be used as a feedstock to produce biochar or hydrochar through pyrolysis or through the HTC process, respectively. Syngas produced from gasification can further be fermented to produce liquid biofuels. The aqueous phase of the HTL process can be utilized to cultivate algae. Biochar from the pyrolysis process can be used as a feedstock in gasification to produce carbon rich syngas. These synergistic approaches result in higher carbon utilization efficiency, minimize wastage, and produce highly valuable bio-products. It also reduces the capital cost and operational cost alongside higher energy and mass closure and paves the way for the circular economy [67,68,69,70].

3. Pros and Cons of Biorefinery Approaches

The execution of second-generation biorefineries comes with various advantages and challenges. Table 2 gives the pros and cons of different second-generation biorefineries. The main advantage of second-generation biorefineries is their dependence on non-food biomass; this promotes food security by utilizing underutilized and plentiful biomass. It also addresses the problem of waste management and environmental issues in the disposal of waste products [71]. The other main advantage is that it addresses the reduction of GHG emissions compared to conventional fossil fuels. It also produces bio-based products, namely bio-char, bioethanol, bio-diesel, biochemicals, and biopolymers, and also produces heat and power, enabling the circular economy [72]. This also paves the way for rural employment, produces additional income for farmers, and reduces dependency on fossil fuels [73].
Second-generation biorefineries also faces challenges like the construction of the plant, as this involves high investment and operational costs. The heterogenous nature of biomass complicates the conversion of biomass into bioenergy and biofuels [74]. The logistics, seasonal availability, and varied composition of biomass also affects the conversion efficiency and quality of the products. The pretreatment of biomass for biorefinery processes, as well as downstream and upstream process, needed to obtain high quality material are an additional hindrance for biorefineries. Non-utilization or non-recovery of by-products can cause environmental problems [75]. For example, pyrogas from the biochar production process and tar from the syngas production process are very harmful if not recovered and utilized properly. The main hinderance is the marketability and wide adoption of these products instead of conventional products.
Table 2. Pros and cons of different second generation biorefineries.
Table 2. Pros and cons of different second generation biorefineries.
TechnologyProsConsTechnology Ready LevelReference
Anaerobic Digestion
  • Yields biogas and bio-digestate (fertilizer)
  • Quick adoption to manage waste effectively
  • Low suitability for heterogenous waste
  • Purification of biogas is required to meet the energy density of fossil fuel
7–9[76,77]
Fermentation
  • Yields high-value bio-chemicals and bioethanol
  • High adaptability of biomass feedstock
  • Costlier pretreatment operation
  • Sensitive technology as it involves microbes
5–7[78,79]
Pyrolysis
  • Feedstock flexibility
  • Easier to integrate with existing facility
  • Energy efficient technology
  • Higher investment
  • Feedstock preparation tedious
  • Problematic condensation and down-streaming operation
5[80]
Gasification
  • Flexibility in feedstock
  • Energy efficient to produce syngas
  • Combined heat and power (CHP) production is possible
  • High investment
  • Requirement of uniform size and dried biomass
  • Tar, slag issues
6–7[80]
Hydrothermal Carbonization (HTC)
  • No requirement of drying wet biomass
  • Biocrude, biochar, syngas can be produced
  • Low temperature operation
  • Energy intensive operation
  • High pressure required
  • Higher investment
5–7[81,82]
Hydrothermal Liquefaction (HTL)
  • No requirement of drying wet biomass
  • Biocrude equivalent to crude oil
  • Energy intensive operation
  • High pressure required
  • Higher investment
4–6[80,83]
Algae-Based Biorefinery
  • Algae can be cultivated in wastewater
  • Higher biomass yield per unit area
  • Biodiesel from lipids and animal feed from protein
  • High carbon sequestration
  • High water required if it is cultivated in fresh water
  • Energy intensive harvesting and drying process
6–7[84,85,86]
Integrated Biorefineries
  • Multiple bioproducts
  • Circular economy
  • Complex design
  • Higher investment and operating cost
5–6[81,87]

4. Assessment of Energy and Bioproducts from Biomass

Second-generation biorefineries deliver a substitute to first-generation feedstocks to produce energy and high value bioproducts in a sustainable way and without affecting food security. The bio-products include platform chemicals, bioplastics, bio-based composites, bio-polymers, and biochar. The moisture, bulk density, energy value, and biochemical composition, namely cellulose, hemicellulose, and lignin content, determine the conversion efficiency and bio-energy potential of biomass [88,89]. Bioenergy products have extensive applications, including as thermal energy, transportation fuels, and for power production [90]. The process also yields high-value bioproducts, namely bio-digestate, biochar, bio-active compounds, organic acids, bioplastics, biopolymers, aromatic chemicals, adhesives, and carbon fibers [91]. Table 3 exemplifies biomass properties with estimated energy generation potential and possible bioproducts using the tool developed by Tamil Nadu Agricultural University [92].

5. Policy Framework for Supporting Biorefinery Development

India’s biorefinery development began in response to the 1970s oil crisis, which spurred the search for alternative renewable energy sources. In the 1980s, the government established the Commission on Additional Sources of Energy under the Department of Science and Technology, which later became the Department of Conventional Energy in 1982. A significant development came in 1987 with the creation of the Indian Renewable Energy Development Agency, which played a key role in advancing renewable energy projects [93]. The National Policy on Biofuels, introduced in 2018, serves as the cornerstone for India’s biorefinery strategy. It categorizes biofuels into basic, advanced, and third-generation types and sets ambitious targets, such as a 20% ethanol blend in petrol and a 5% biodiesel blend by 2030. The policy also expands the range of feedstocks for biofuel production, including damaged food grains and lignocellulosic biomass [94].
To promote lignocellulosic biorefineries, the JI-VAN Initiative was launched, providing financial aid and fostering technological advancements [95]. Measures such as Viability Gap Funding (50,000 million INR over six years), 100% foreign direct investment allowances, and central tax exemptions support these efforts. Additionally, the Minimum Purchase Price mechanism ensures the commercial feasibility of bioethanol and biodiesel [96].
India’s institutional framework for biofuels operates on multiple levels, with the National Biofuel Coordination Committee, led by the Prime Minister, at the helm. The Biofuel Steering Committee, reporting to the Cabinet Secretary, provides further support. At the regional level, biofuel boards are responsible for overseeing the implementation of biofuel initiatives, though coordination between states continues to present significant challenges [97,98].
Several ministries contribute to the policy’s execution [96]:
  • Ministry of New and Renewable Energy (MNRE): Formulates overarching policies and provides research support.
  • Ministry of Petroleum and Natural Gas (MoPNG): Oversees marketing, pricing, and procurement.
  • Ministry of Agriculture (MoA): Conducts feedstock research.
  • Ministry of Rural Development (MoRD) and Ministry of Panchayati Raj (MoPR): Promote Jatropha and other plantation initiatives on wastelands.
  • Ministry of Science and Technology (MoS&T): Focuses on non-edible oil feedstocks.
  • Ministry of Environment and Forests (MoEF): Monitors environmental impacts.
  • Ministry of Finance (MoF): Provides financial incentives.
This integrated framework ensures a comprehensive approach to biofuel development, though better coordination between central and state policies is essential.
India’s agricultural sector generates substantial crop residues, often managed through open burning, contributing to air pollution. The National Policy for Management of Crop Residue (NPMCR) 2014 promotes in situ residue management technologies, satellite monitoring, and financial support for farmers. However, implementation has been limited to states such as Punjab, Haryana, and Rajasthan.
The National Green Tribunal’s ban on crop residue burning in four states and the promotion of mechanized solutions, such as turbo happy seeders and Super-Straw Management Systems, have mitigated residue burning to some extent. Despite this, challenges persist, with significant residues still burned; 50% of Punjab’s and 16.9% of Haryana’s rice straw residues were burned in situ during 2018–2019 [99].
Central and state governments have initiated several policies to promote bioenergy from crop residues:
  • Punjab’s 2012 Energy Policy targeted 600 MW of biomass power by 2022 but achieved only 62.5 MW by 2020.
  • Haryana’s 2018 Bioenergy Policy aimed for 150 MW but showed limited progress.
Central initiatives include biomass co-firing in coal plants and lignocellulosic ethanol plants developed by Indian Oil Corporation and Hindustan Petroleum. These plants are projected to utilize 57.7 Mt of crop residues annually, leaving a surplus of 120 Mt unaddressed [99].

6. State-Level Bioenergy Development Initiatives

State-level efforts in bioenergy development remain uneven. States like Gujarat and Uttar Pradesh are pioneering innovative policies. Gujarat’s Waste-to-Energy Policy and Uttar Pradesh’s Bioenergy Development Board exemplify progressive approaches to bioenergy. Conversely, states such as Jharkhand and Chhattisgarh have limited diversification in bioenergy projects. Table 4 summarizes key state-level bioenergy initiatives.
Table 4. State-wise Summary of Bioenergy Development in India [96,100].
Table 4. State-wise Summary of Bioenergy Development in India [96,100].
State/Union TerritoryKey Activities and InitiativesRemarksSource
PunjabBiogas from agro-waste, gasification, co-generation in sugar mills.Proactive state with remarkable agro-waste energy production.[101]
HaryanaBiofuels, bioenergy, and biogas programs, along with both grid-connected and off-grid initiatives.Programs are well-directed and regularly upgraded.[102]
Uttar PradeshBioenergy Development Board; biogas, biodiesel, and bioethanol missions.Effective grassroots-level programs.[103]
RajasthanBiomass power, biogas, forest department involvement.Policies need updating but cumulative efforts are reliable.[104]
GujaratWaste-to-Energy Policy, biomass power, co-generation projects.Proactive state; innovative waste-to-energy policy.[105]
Madhya PradeshGrid-connected and off-grid biomass projects.Significant private-sector involvement.[106]
JharkhandBiogas and biomass power programs.Limited diversification in bioenergy projects.[107]
ChhattisgarhPolicy-based incentives for bioenergy.Information on bioenergy options is limited.[108]
TelanganaBiomass and biogas programs, spanning from cooking applications to megawatt-scale power generation.Appreciable efforts for rural and urban regions.[109]
Andhra PradeshBiomass-based captive power in sugar mills.Active in bioenergy development.[110]
KarnatakaBiogas, combustion, and co-generation schemes.Well-planned bioenergy development direction.[111]
Tamil NaduWaste-to-energy, biogas, and gasification projects.Effective grid-connected urban initiatives.[112]
MaharashtraIncentives for biomass briquettes and waste-to-energy projects.Comprehensive decentralized bioenergy policy.[113]
OdishaImproved cook stoves, biomass gasification.Cumulative incentive-based schemes.[114]
West BengalBiogas production, village energy security programs.Significant urban MSW-to-energy efforts.[115]
TripuraBiogas plants and improved cook stoves (Unnat Chulha).Ground-level initiatives are commendable.[116]
SikkimRenewable energy nodal agency.Limited information on bioenergy activities.[117]
NagalandFinancial support for Unnat Chulha and NBMMP.Focused on grassroots-level clean energy.[118]
MeghalayaSubsidies for Unnat Chulha and NBMMP.Basic bioenergy initiatives.[119]
KeralaBiogas plant setups under NBMMP.Well-organized renewable energy programs.[120]
AssamBiogas and biomass gasification programs.High potential for bioenergy.[121]
ChandigarhMSW-to-energy projects.Efficient urban waste management for energy.[122]
The framework for biorefinery development in India emphasizes technological advancements to support the biofuel sector. Key initiatives include the promotion of pilot projects aimed at testing and optimizing biorefinery processes. These pilot projects act as a testing ground for refining technologies and scaling up production, laying the groundwork for broader industrial applications. Moreover, the framework fosters industry-academia partnerships, which play a pivotal role in advancing research and development. Collaboration between academic institutions and industrial players ensures the seamless transfer of knowledge and the integration of cutting-edge innovations into practical applications. Additionally, international collaborations have been prioritized to facilitate the transfer of global expertise and advanced technologies, further bolstering the sector’s growth. Specific focus has been placed on enzyme development and the creation of indigenous technologies, which are critical for enhancing the efficiency and sustainability of biofuel production processes [123,124].
Despite these advancements, several challenges persist, particularly in infrastructure development and technology optimization. Many biorefineries face hurdles in establishing the necessary infrastructure to support large-scale operations. Technological refinement is another pressing issue, as efforts to improve efficiency and scalability remain ongoing. Nonetheless, the framework has made notable achievements, including the establishment of multiple 100 Kiloliters per Day commercial-scale biorefinery plants. These facilities demonstrate the feasibility of large-scale biofuel production, marking a significant step forward for the sector. Furthermore, the initiatives have yielded substantial environmental benefits, such as a reduction in crop burning incidents, which helps mitigate air pollution and aligns with broader environmental sustainability goals. Another critical outcome is the creation of employment opportunities in rural areas, contributing to the socio-economic development of these regions [94,98].
Looking ahead, India’s biorefinery policy framework continues to evolve with an emphasis on sustainability and long-term impact. Enhanced technological support remains a priority, with efforts focused on advancing biorefinery technologies and improving their integration into existing systems. The framework also highlights the importance of supply chain management, aiming to optimize the collection, storage, and distribution of feedstock materials. In parallel, the development of robust markets for biofuels is being pursued to ensure the economic viability of the sector. A critical aspect of the future outlook involves the integration of state-level initiatives with central government policies. This harmonization aims to create a cohesive policy environment that leverages regional strengths while aligning with national objectives. Such measures are essential for achieving India’s renewable energy goals and establishing a sustainable bioeconomy [94]. Figure 2 depicts renewable flow management, emphasizing efficient bio-resource use for sustainable fuels.

7. Impact on the Environment, Economy, and Energy Sectors

7.1. Environment

Second-generation biorefineries in India present substantial environmental advantages over traditional fossil fuel systems. By prioritizing the use of lignocellulosic biomass rather than food-based crops, these biorefineries contribute to sustainability while reducing competition for agricultural resources. The shift towards second-generation biofuels aligns with India’s broader environmental objectives, significantly lowering GHG emissions and minimizing reliance on fossil fuels. Biofuels derived from lignocellulosic feedstocks are considered near carbon-neutral, as the carbon dioxide released during combustion is counterbalanced by carbon sequestration during plant growth [126].
When these compounds are combusted, they release the stored energy and return CO2 to the atmosphere, creating a carbon-neutral cycle that significantly reduces net GHG emissions compared to fossil fuels. Biomass currently accounts for approximately 14% of global energy consumption, with developing nations utilizing 38% of this energy, particularly in rural areas where access to conventional energy sources remains limited [2]. India, with its favorable climate and extensive agricultural activities, possesses abundant biomass resources that present significant opportunities for sustainable energy production and utilization.
Traditional approaches to biomass utilization have focused primarily on single-product systems, such as dedicated bioethanol or biogas production facilities. However, these approaches often fail to maximize the value of biomass factors. Table 5 summarizes the key environmental advantages of second-generation biorefineries, highlighting their role in reducing GHG emissions, enhancing resource efficiency, and promoting sustainability through innovative waste management and conservation strategies.

7.2. Economy

Second-generation biorefineries play a crucial role in reducing India’s dependence on fossil fuel imports, thereby enhancing national energy security. With an annual agricultural waste production of approximately 1043 million metric tons, India possesses a substantial feedstock base for biofuel generation. This biomass has the potential to yield around 64 billion litres of bioethanol annually, aligning with government initiatives aimed at promoting renewable energy and attracting industrial investments [127].
India’s bioethanol market, valued at USD 2.35 billion in 2023, is anticipated to double by 2030, growing at a compound annual growth rate (CAGR) of 8.7%. Additionally, the biomethane and biohydrogen markets, valued at USD 4.2 billion and USD 1.47 billion, respectively, demonstrate significant growth potential [128]. The influx of private investments has been a key driver of this expansion, with major industrial players such as Reliance Industries and the Adani Group investing heavily in the sector. Notably, the Adani Group has pledged an estimated USD 50 billion toward biohydrogen production and the development of sustainable energy infrastructure [129].
Beyond energy security, biorefineries contribute to rural economic development by generating employment and producing high-value biochemical by-products such as furfurals, xylitol, and organic acids. The integration of a circular economy model further enhances profitability by repurposing agricultural residues, mitigating both environmental and economic losses linked to conventional waste disposal practices [97]. Table 6 highlights the key economic advantages of second-generation biorefineries, including market growth and investment.
The expansion of second-generation biorefineries in India is poised to drive long-term economic sustainability. Continued advancements in biofuel technology, integration of renewable energy sources, and supportive government policies will further strengthen this sector’s contribution to energy security and economic development. Additionally, increased focus on research and innovation in enzyme-based conversion processes and biomass valorization will optimize the economic benefits of biorefineries while ensuring environmental sustainability [127,130].

7.3. Energy

India’s shift toward biomass-based energy solutions is a key response to its growing energy demands, which increased from 6101 Mtoe in 1973 to 13,699 Mtoe in 2016 [96,131]. The development of second-generation biorefineries is poised to contribute significantly to reducing GHG emissions, with potential reductions of up to 2.7% of GDP by 2030, supporting India’s commitments under the Paris Agreement [132].
Solar energy integration into biorefinery operations has proven highly effective, harnessing India’s vast annual solar potential, which exceeds 5000 trillion kWh [133]. Additionally, Combined Heat and Power (CHP) systems have been integrated into biorefineries, optimizing resource utilization and resulting in lower environmental impacts compared to conventional energy systems [134]. The strategic placement of biorefineries helps minimize transportation costs, which can account for up to 20% of operational expenses. Geographical variations in biomass availability require region-specific solutions to ensure cost-effectiveness and operational efficiency [135,136]. The integration of CHP systems in biorefineries further enhances energy efficiency. These systems can achieve 80–90% overall efficiency, compared to the 30–40% efficiency seen in conventional power generation systems [134]. Table 7 summarizes the critical factors influencing India’s transition to biomass-based energy solutions

7.4. Life Cycle Analysis (LCA)

Life Cycle Analysis (LCA) provides a detailed evaluation of the environmental performance of biorefinery systems, analyzing their entire value chain. Studies conducted in India have highlighted several key findings in LCA:
  • Carbon Footprint Reduction: Bio-derived products consistently demonstrate lower GHG emissions compared to fossil-based alternatives. For example, bio-derived polyethylene reduces emissions by 0.75 kg CO2-eq/kg compared to conventional petrochemical processes [137].
  • Process Optimization: Advances in production methods have significantly decreased environmental impacts. Optimized charcoal value chains, for instance, reduced emissions from 2.15 CO2-eq to 0.50 CO2-eq through improved processes and better resource utilization [138].
  • Holistic Impact Assessment: LCA studies assess environmental impacts beyond carbon emissions, including water quality, land use, biodiversity, and human health.
  • Technology Comparison: LCA facilitates comparisons between different conversion pathways. Biochemical routes often show advantages in water-related impacts, while thermochemical pathways may excel in energy efficiency.
The integration of circular economy principles within LCA frameworks has led to the development of closed-loop systems that maximize resource recovery and minimize waste. For example, lignin residues from bioethanol production are increasingly being repurposed into high-value applications such as bio-composites, pharmaceuticals, and biosensors [139].

7.5. Circular Economy

The circular economy approach has the potential to significantly transform India’s biorefinery sector. This approach systematically designs out waste and pollution, keeps materials in productive use, and regenerates natural systems. Key aspects of circular economy integration include:
  • Resource Efficiency: Circular biorefinery models have demonstrated significant improvements in resource use, with some systems achieving near-zero waste through cascading biomass components [140].
  • Environmental Performance: Circular approaches have been shown to reduce GHG emissions by 39–86% and decrease non-renewable energy usage by 65% compared to linear production models [137].
  • Economic Value Creation: The circular bioeconomy creates new revenue streams by revalorizing materials previously considered waste. For example, lignin valorization has applications in polymers, bio-composites, and nanomaterials, with global markets projected to reach USD 1.2 billion by 2025 [139].
  • Rural Development: Circular biorefinery models stimulate rural economies by establishing collection centers, preprocessing facilities, and local value-addition activities.
  • Social Inclusion: These models also promote social inclusion by incorporating traditional knowledge and providing marginalized communities with opportunities to participate in biorefinery value chains.
The adoption of circular economy principles ensures that India’s biorefinery sector promotes sustainability on environmental, economic, and social fronts. This holistic approach aligns with the United Nations Sustainable Development Goals while addressing challenges in waste management, resource efficiency, and inclusive development [141]. Innovations in India’s circular bioeconomy include integrated biorefineries that produce multiple products from a single feedstock, agricultural practices that return nutrients to soil via biochar and digestate, and collaborative models linking urban waste generators with rural biomass processors. Table 8 provides an overview of the key environmental, economic, and social impacts of integrating LCA and circular economy principles in India’s biorefinery sector.

8. Roadmap to Implement Biorefinery Approach

Implementing biorefineries to maximize biomass valorization requires a multi-disciplinary approach that integrates bio-engineering, chemistry, and agricultural sciences. In India, where agricultural residues and other biomass types are abundant, the potential for second-generation biorefineries is substantial. This roadmap highlights the strategic integration of technologies and policies needed to realize this potential, focusing on thermochemical and biochemical conversion pathways [132].
Biorefineries represent a transformative approach to achieving sustainability and economic viability in bio-based industries. This guide outlines six critical steps for developing and optimizing biorefineries, ensuring they meet environmental, economic, and policy objectives.
  • Process Development and Optimization: This stage focuses on improving biorefinery efficiency and sustainability by optimizing feedstock cultivation, processing, and product recovery to reduce GHG emissions and non-renewable energy use [142]. Optimization of the entire value chain is essential to achieving cost-effectiveness and economic viability.
  • Supply Chain Development: Effective supply chain management ensures the smooth delivery of biomass to the biorefinery. Selecting strategic locations minimizes transportation costs, while optimizing biomass production and developing efficient logistics systems improve the overall operational efficiency of the supply chain [135].
  • Integration with Existing Infrastructure: Biorefineries can enhance their capabilities by integrating with existing petrochemical plants, creating hybrid systems. Utilizing advanced biotechnology enables the seamless adaptation of current infrastructure, bridging gaps and maximizing resource utilization [143].
  • Economic Viability and Revenue Diversification: To achieve financial sustainability, biorefineries must diversify their revenue streams. Producing high-value biochemicals alongside biofuels, generating energy for self-sustaining operations, and exploring additional revenue opportunities are critical to their long-term success [144].
  • Policy and Regulatory Support: A robust and stable policy framework is essential for fostering growth in biorefinery projects. Clear subsidies, legal guidelines, and mandates are needed to inspire confidence among investors and ensure compliance with environmental and economic objectives [96].
  • Environmental Monitoring and Circular Economy: Monitoring and reducing the environmental impact of biorefineries is a cornerstone of their development. Implementing life cycle assessments and adopting circular economy principles, such as resource recovery and closed-loop systems, ensures sustainability and minimizes waste [145].

Step-by-Step Roadmap for Biorefinery Development and Optimization

  • Identify Objectives and Goals: Define the primary objectives, such as reducing GHG emissions, improving sustainability, and achieving economic viability. Align goals with global and regional sustainability [96].
  • Conduct Feasibility Studies: Evaluate the availability of biomass feedstocks and their environmental impact. Assess market demand for bio-based products and energy [135].
  • Develop Process Design and Optimization: Design efficient processes for feedstock cultivation, processing, and product recovery. Incorporate advanced technologies to maximize energy efficiency and minimize waste [141].
  • Build an Efficient Supply Chain: Choose strategic locations to reduce transportation costs. Optimize biomass production and logistics for collection, transport, and preprocessing [135].
  • Integrate with Existing Infrastructure: Develop hybrid systems that combine biorefineries with petrochemical plants. Utilize biotechnology to bridge gaps and enhance operational efficiency [143].
  • Establish Economic Models: Create a financial plan that includes high-value biochemicals, biofuels, and self-sustaining energy generation. Diversify revenue streams to ensure long-term viability [144].
  • Engage Policy and Regulatory Stakeholders: Work with policymakers to establish subsidies, mandates, and guidelines. Foster investor confidence by ensuring regulatory compliance [96].
  • Implement Environmental Monitoring and Sustainability Practices: Conduct life cycle assessments to track environmental impact. Apply circular economy principles like resource recovery and closed-loop systems [145].
  • Pilot and Scale-Up: Launch pilot projects to validate designs and processes. Scale up operations based on pilot results, ensuring efficiency and sustainability.
  • Continuous Improvement and Innovation: Regularly review and refine processes to incorporate technological advancements. Monitor market trends to adapt products and services accordingly.

9. Challenges

India faces unique challenges and opportunities in adopting second-generation biofuels. Current production is dominated by first-generation biofuels, including sugarcane and Jatropha, which are insufficient to meet the National Policy on Biofuels (NPB) target of 20% blending by 2030. Achieving these targets will require transitioning to lignocellulosic ethanol and biomass-to-liquid (BTL) biodiesel technologies, supported by robust research and development and industrial-scale deployment.
Second-Generation Biofuels: A single demonstration plant in Pune, Maharashtra, processes 100 dry tons of biomass per day, including residues like corn stover and bagasse. However, scaling these technologies remains a challenge due to cost and infrastructure limitations. By 2030, it is estimated that India can produce 50 billion litres of biofuels from agricultural residues, meeting the 20% blending target [132].
Feedstock Challenges: Limited availability of dedicated energy crops and the unsustainable use of sugarcane molasses highlight the need for diversified feedstock collection mechanisms [146].
Investment Needs: Transitioning to second-generation biofuels under a Business-As-Usual (BAU) scenario requires USD 2 billion by 2030, while achieving NPB goals necessitates USD 32 billion in cumulative investments [132].

10. Conclusions

This study highlights the significant contributions of second-generation biorefineries in the sustainable energy transition, with a particular focus on India. The research shows that second-generation biorefineries can effectively utilize non-food biomass feedstocks, such as crop residues and agro-processing waste, for the production of biofuels, biochemicals, and bio-based products. Through the integration of biochemical and thermochemical conversion technologies, these biorefineries not only help in reducing greenhouse gas emissions but also contribute to energy security and waste minimization. Notably, bioethanol, biogas, and biohydrogen production from these sources can significantly support India’s renewable energy goals, including the target of a 20% ethanol blend by 2025.
The study demonstrates the importance of government policies such as India’s National Biofuels Policy, which provides a robust framework for promoting biorefinery development and advancing bioethanol production. The research also shows the potential for rural economic growth, as biorefineries can generate jobs and produce high-value by-products like furfurals, xylitol, and organic acids, which help to promote a circular economy.
However, several challenges remain, such as the high variability in biomass feedstock properties, difficulties in process integration, and supply chain inefficiencies. Despite these limitations, the findings indicate that second-generation biorefineries, when optimized, have a strong potential to be economically viable. For instance, the bamboo-based bioethanol refinery in Assam and the lignocellulosic biorefinery in Karnataka provide promising models of large-scale implementation, demonstrating that with proper investment and technological advancements, biorefineries can become sustainable economic drivers.
Future research should focus on overcoming these barriers by improving biomass feedstock pretreatment processes and fermentation efficiencies. Furthermore, the integration of advanced technologies, such as IoT-enabled monitoring systems and machine learning, could be explored to enhance operational efficiencies and sustainability. Additionally, international comparisons of biorefinery technologies, policies, and market dynamics could offer valuable insights for accelerating the global adoption of second-generation biorefineries.

Author Contributions

Conceptualization, A.N.T. and M.G.; methodology, A.N.T. and M.G.; software, A.N.T.; validation, A.N.T., M.G. and G.J.; formal analysis, A.N.T. and M.G.; investigation, A.N.T. and M.G.; resources, M.G.; data curation, M.G.; writing—original draft preparation, A.N.T. and M.G.; writing—review and editing, G.J., S.V., S.K., D.R. and S.S.; visualization, D.R. and S.S.; supervision, D.R. and S.S.; project administration, D.R. and S.S.; funding acquisition, D.R. and S.S. All authors have read and agreed to the published version of the manuscript.

Funding

This research received no external funding.

Acknowledgments

The authors would like to thank TSP/Royal Academy of Engineering, UK/Dated. 01.11.2023 (TSP-2325-5-IN/159) funding to support this work was provided through the Royal Academy of Engineering, United Kingdom.

Conflicts of Interest

The authors declare no conflicts of interest.

Abbreviations

The following abbreviations are used in this manuscript:
LCALife Cycle Analysis
GDPGross domestic product
GHGGreenhouse Gas
HTCHydrothermal Carbonization
HTLHydrothermal Liquefaction
CHPCombined Heat and Power
MNREMinistry of New and Renewable Energy
MoPNGMinistry of Petroleum and Natural Gas
MoAMinistry of Agriculture
MoRDMinistry of Rural Development
MoPRMinistry of Panchayati Raj
MoS&TMinistry of Science and Technology
MoEFMinistry of Environment and Forests
MoFMinistry of Finance
NPMCRThe National Policy for Management of Crop Residue
CAGRCompound Annual Growth Rate
BAUBusiness-As-Usual
NPBNational Policy on Biofuels
BTLBiomass-To-Liquid

References

  1. Ajala, E.O.; Ighalo, J.O.; Ajala, M.A.; Adeniyi, A.G.; Ayanshola, A.M. Sugarcane Bagasse: A Biomass Sufficiently Applied for Improving Global Energy, Environment and Economic Sustainability. Bioresour. Bioprocess. 2021, 8, 87. [Google Scholar] [CrossRef]
  2. Sudha, P.; Ravindranath, N.H. Land Availability and Biomass Production Potential in India. Biomass Bioenergy 1999, 16, 207–221. [Google Scholar] [CrossRef]
  3. Koul, B.; Yakoob, M.; Shah, M.P. Agricultural Waste Management Strategies for Environmental Sustainability. Environ. Res. 2022, 206, 112285. [Google Scholar] [CrossRef]
  4. Central Pollution Control Board (CPCB); Delhi. 2021. Available online: https://cpcb.nic.in/openpdffile.php?id=UmVwb3J0RmlsZXMvMTQwM18xNjU1MzU0NzkxX21lZGlhcGhvdG8xNjQ3MS5wZGY= (accessed on 8 February 2025).
  5. MOEFCC. 2021. Available online: https://fsi.nic.in/isfr-2021/chapter-9.pdf (accessed on 8 February 2025).
  6. Solomon, S.; Swapna, M. Indian Sugar Industry: Towards Self-Reliance for Sustainability. Sugar Tech. 2022, 24, 630–650. [Google Scholar] [CrossRef] [PubMed]
  7. Saravanan, A.; Senthil Kumar, P.; Badawi, M.; Mohanakrishna, G.; Aminabhavi, T.M. Valorization of Micro-Algae Biomass for the Development of Green Biorefinery: Perspectives on Techno-Economic Analysis and the Way towards Sustainability. Chem. Eng. J. 2023, 453, 139754. [Google Scholar] [CrossRef]
  8. Bassoli, S.C.; da Fonseca, Y.A.; Wandurraga, H.J.L.; Baeta, B.E.L.; de Souza Amaral, M. Research Progress, Trends, and Future Prospects on Hydrothermal Liquefaction of Algae for Biocrude Production: A Bibliometric Analysis. Biomass Convers. Biorefinery 2024, 14, 28781–28796. [Google Scholar] [CrossRef]
  9. Ning, P.; Yang, G.; Hu, L.; Sun, J.; Shi, L.; Zhou, Y.; Wang, Z.; Yang, J. Recent Advances in the Valorization of Plant Biomass. Biotechnol. Biofuels 2021, 14, 102. [Google Scholar] [CrossRef]
  10. Song, B.; Lin, R.; Lam, C.H.; Wu, H.; Tsui, T.-H.; Yu, Y. Recent Advances and Challenges of Inter-Disciplinary Biomass Valorization by Integrating Hydrothermal and Biological Techniques. Renew. Sustain. Energy Rev. 2021, 135, 110370. [Google Scholar] [CrossRef]
  11. Ghamari, M.; Suvish; Hwang See, C.; Yu, H.; Anitha, T.; Balamurugan, V.T.; Velusamy, S.; Hughes, D.; Sundaram, S. Nanocellulose Extraction from Biomass Waste: Unlocking Sustainable Pathways for Biomedical Applications. Chem. Rec. 2025, Online ahead of print, e202400249. [Google Scholar] [CrossRef]
  12. Liakakou, E.T.; Vreugdenhil, B.J.; Cerone, N.; Zimbardi, F.; Pinto, F.; André, R.; Marques, P.; Mata, R.; Girio, F. Gasification of Lignin-Rich Residues for the Production of Biofuels via Syngas Fermentation: Comparison of Gasification Technologies. Fuel 2019, 251, 580–592. [Google Scholar] [CrossRef]
  13. Quinn, J.C.; Yates, T.; Douglas, N.; Weyer, K.; Butler, J.; Bradley, T.H.; Lammers, P.J. Nannochloropsis Production Metrics in a Scalable Outdoor Photobioreactor for Commercial Applications. Bioresour. Technol. 2012, 117, 164–171. [Google Scholar] [CrossRef]
  14. Schmidt, K.N.; Zou, C.B.; Kakani, V.G.; Zhong, Y.; Will, R.E. Improved Productivity, Water Yield, and Water Use Efficiency by Incorporating Switchgrass Cultivation and Native Ecosystems in an Integrated Biofuel Feedstock System. GCB Bioenergy 2021, 13, 369–381. [Google Scholar] [CrossRef]
  15. Kolarić, L.; Popović, V.; Ikanović, J.; Živanović, L.; Janković, S.; Rakašćan, N.; Stevanović, P. Productivity of Soybean and the Possibility of Using It as Energy. Sel. I Semen. 2023, 29, 51–59. [Google Scholar] [CrossRef]
  16. Booth, T.H.; Raison, R.J.; Crawford, D.F.; Jovanovic, T.; O’Connor, M.H.; Raisbeck-Brown, N.; O’Connell, D.A.; Hogg, B.W.; Lee, D.J. Biomass for Aviation Fuel Production in the Fitzroy Basin, Queensland: A Preliminary Assessment of Native and Plantation Forest Potential. Aust. For. 2014, 77, 1–8. [Google Scholar] [CrossRef]
  17. Yancey, N.A.; Tumuluru, J.S.; Wright, C.T. Drying, Grinding and Pelletization Studies on Raw and Formulated Biomass Feedstock’s for Bioenergy Applications. J. Biobased Mater. Bioenergy 2013, 7, 549–558. [Google Scholar] [CrossRef]
  18. Börjesson, P.; Hansson, J.; Berndes, G. Future Demand for Forest-Based Biomass for Energy Purposes in Sweden. For. Ecol. Manag. 2017, 383, 17–26. [Google Scholar] [CrossRef]
  19. Mignogna, D.; Szabó, M.; Ceci, P.; Avino, P. Biomass Energy and Biofuels: Perspective, Potentials, and Challenges in the Energy Transition. Sustainability 2024, 16, 7036. [Google Scholar] [CrossRef]
  20. Natarajan, K.; Latva-Käyrä, P.; Zyadin, A.; Chauhan, S.; Singh, H.; Pappinen, A.; Pelkonen, P. Biomass Resource Assessment and Existing Biomass Use in the Madhya Pradesh, Maharashtra, and Tamil Nadu States of India. Challenges 2015, 6, 158–172. [Google Scholar] [CrossRef]
  21. Cvetković, S.M.; Radoičić, T.K.; Kijevčanin, M.; Novaković, J.G. Life Cycle Energy Assessment of Biohydrogen Production via Biogas Steam Reforming: Case Study of Biogas Plant on a Farm in Serbia. Int. J. Hydrogen Energy 2021, 46, 14130–14137. [Google Scholar] [CrossRef]
  22. Suhartini, S.; Pangestuti, M.B.; Elviliana; Rohma, N.A.; Junaidi, M.A.; Paul, R.; Nurika, I.; Rahmah, N.L.; Melville, L. Valorisation of Macroalgae for Biofuels in Indonesia: An Integrated Biorefinery Approach. Environ. Technol. Rev. 2024, 13, 269–304. [Google Scholar] [CrossRef]
  23. Gupta, A.; Thengane, S.K.; Mahajani, S. Kinetics of Pyrolysis and Gasification of Cotton Stalk in the Central Parts of India. Fuel 2020, 263, 116752. [Google Scholar] [CrossRef]
  24. Jafri, N.; Wong, W.Y.; Doshi, V.; Yoon, L.W.; Cheah, K.H. A Review on Production and Characterization of Biochars for Application in Direct Carbon Fuel Cells. Process Saf. Environ. Prot. 2018, 118, 152–166. [Google Scholar] [CrossRef]
  25. Legonda, I.A. Biomass Gasification Using a Horizontal Entrained-Flow Gasifier and Catalytic Processing of the Product Gas. Ph.D. Thesis, Cardiff University, Cardiff, UK, 2012. [Google Scholar]
  26. Liu, Z.; Quek, A.; Balasubramanian, R. Preparation and Characterization of Fuel Pellets from Woody Biomass, Agro-Residues and Their Corresponding Hydrochars. Appl. Energy 2014, 113, 1315–1322. [Google Scholar] [CrossRef]
  27. Rajagopal, J.; Gopinath, K.P.; Neha, R.; Aakriti, K.; Jayaraman, R.S.; Arun, J.; Pugazhendhi, A. Processing of Household Waste via Hydrothermal Gasification and Hydrothermal Liquefaction for Bio-Oil and Bio-Hydrogen Production: Comparison with RSM Studies. J. Environ. Chem. Eng. 2022, 10, 107218. [Google Scholar] [CrossRef]
  28. Güleç, F.; Parthiban, A.; Umenweke, G.C.; Musa, U.; Williams, O.; Mortezaei, Y.; Suk-Oh, H.; Lester, E.; Ogbaga, C.C.; Gunes, B.; et al. Progress in Lignocellulosic Biomass Valorization for Biofuels and Value-Added Chemical Production in the EU: A Focus on Thermochemical Conversion Processes. Biofuels Bioprod. Biorefining 2024, 18, 755–781. [Google Scholar] [CrossRef]
  29. Alavijeh, R.S.; Shahvandi, A.; Okoro, O.V.; Denayer, J.F.M.; Karimi, K. Biorefining of Corn Stover for Efficient Production of Bioethanol, Biodiesel, Biomethane, and Value-Added Byproducts. Energy Convers. Manag. 2023, 283, 116877. [Google Scholar] [CrossRef]
  30. Zhao, Y.; Damgaard, A.; Christensen, T.H. Bioethanol from Corn Stover—A Review and Technical Assessment of Alternative Biotechnologies. Prog. Energy Combust. Sci. 2018, 67, 275–291. [Google Scholar] [CrossRef]
  31. Yong, K.J.; Wu, T.Y.; Lee, C.B.T.L.; Lee, Z.J.; Liu, Q.; Jahim, J.M.; Zhou, Q.; Zhang, L. Furfural Production from Biomass Residues: Current Technologies, Challenges and Future Prospects. Biomass Bioenergy 2022, 161, 106458. [Google Scholar] [CrossRef]
  32. Isah, S.; Ozbay, G. Valorization of Food Loss and Wastes: Feedstocks for Biofuels and Valuable Chemicals. Front. Sustain. Food Syst. 2020, 4, 82. [Google Scholar] [CrossRef]
  33. Chen, S.-J.; Chen, X.; Zhu, M.-J. Xylose Recovery and Bioethanol Production from Sugarcane Bagasse Pretreated by Mild Two-Stage Ultrasonic Assisted Dilute Acid. Bioresour. Technol. 2022, 345, 126463. [Google Scholar] [CrossRef]
  34. Bolivar-Telleria, M.; Turbay, C.; Favarato, L.; Carneiro, T.; de Biasi, R.S.; Fernandes, A.A.R.; Santos, A.M.C.; Fernandes, P.M.B. Second-Generation Bioethanol from Coconut Husk. Biomed. Res. Int. 2018, 2018, 4916497. [Google Scholar] [CrossRef] [PubMed]
  35. Geetha Thanuja, K.; Marimuthu, S.; Ramesh, D.; Karthikeyan, S. Paddy Straw-Based Circular Economy for Sustainable Waste Management. In Handbook of Solid Waste Management; Springer Nature: Singapore, 2022; pp. 683–710. [Google Scholar]
  36. Swain, M.R.; Singh, A.; Sharma, A.K.; Tuli, D.K. Bioethanol Production from Rice-And Wheat Straw: An Overview. In Bioethanol Production from Food Crops; Elsevier: Amsterdam, The Netherlands, 2019; pp. 213–231. [Google Scholar]
  37. Morales-Vera, R.; Vásquez-Ibarra, L.; Scott, F.; Puettmann, M.; Gustafson, R. Life Cycle Assessment of Bioethanol Production: A Case Study from Poplar Biomass Growth in the U.S. Pacific Northwest. Fermentation 2022, 8, 734. [Google Scholar] [CrossRef]
  38. Xu, F.; Sun, D.; Wang, Z.; Li, M.; Yin, X.; Li, H.; Xu, L.; Zhao, J.; Bao, X. Highly Efficient Production of Cellulosic Ethanol from Poplar Using an Optimal C6/C5 Co-Fermentation Strain of Saccharomyces Cerevisiae. Microorganisms 2024, 12, 1174. [Google Scholar] [CrossRef]
  39. Ligero, P.; Villaverde, J.J.; de Vega, A.; Bao, M. Delignification of Eucalyptus Globulus Saplings in Two Organosolv Systems (Formic and Acetic Acid). Ind. Crops Prod. 2008, 27, 110–117. [Google Scholar] [CrossRef]
  40. Hozman-Manrique, A.S.; Garcia-Brand, A.J.; Hernández-Carrión, M.; Porras, A. Isolation and Characterization of Cellulose Microfibers from Colombian Cocoa Pod Husk via Chemical Treatment with Pressure Effects. Polymers 2023, 15, 664. [Google Scholar] [CrossRef]
  41. Ingale, S.; Joshi, S.J.; Gupte, A. Production of Bioethanol Using Agricultural Waste: Banana Pseudo Stem. Braz. J. Microbiol. 2014, 45, 885–892. [Google Scholar] [CrossRef] [PubMed]
  42. Singh, P.K.; Mohanty, P.; Mishra, S.; Adhya, T.K. Food Waste Valorisation for Biogas-Based Bioenergy Production in Circular Bioeconomy: Opportunities, Challenges, and Future Developments. Front. Energy Res. 2022, 10, 903775. [Google Scholar] [CrossRef]
  43. Mahish, P.K.; Verma, D.K.; Ghritlahare, A.; Arora, C.; Otero, P. Microbial Bioconversion of Food Waste to Bio-Fertilizers. Sustain. Food Technol. 2024, 2, 689–708. [Google Scholar] [CrossRef]
  44. Bibra, M.; Samanta, D.; Sharma, N.K.; Singh, G.; Johnson, G.R.; Sani, R.K. Food Waste to Bioethanol: Opportunities and Challenges. Fermentation 2022, 9, 8. [Google Scholar] [CrossRef]
  45. Igliński, B.; Kujawski, W.; Kiełkowska, U. Pyrolysis of Waste Biomass: Technical and Process Achievements, and Future Development—A Review. Energies 2023, 16, 1829. [Google Scholar] [CrossRef]
  46. Matamba, T.; Tahmasebi, A.; Yu, J.; Keshavarz, A.; Abid, H.R.; Iglauer, S. A Review on Biomass as a Substitute Energy Source: Polygeneration Influence and Hydrogen Rich Gas Formation via Pyrolysis. J. Anal. Appl. Pyrolysis 2023, 175, 106221. [Google Scholar] [CrossRef]
  47. Muradov, N.; Fidalgo, B.; Gujar, A.C.; T-Raissi, A. Pyrolysis of Fast-Growing Aquatic Biomass—Lemna Minor (Duckweed): Characterization of Pyrolysis Products. Bioresour. Technol. 2010, 101, 8424–8428. [Google Scholar] [CrossRef]
  48. Wauton, I.; Ogbeide, S.E. Characterization of Pyrolytic Bio-Oil from Water Hyacinth (Eichhornia crassipes) Pyrolysis in a Fixed Bed Reactor. Biofuels 2021, 12, 899–904. [Google Scholar] [CrossRef]
  49. Mitu, M.; Razus, D.; Boldor, D.; Marculescu, C. Flammability Properties of the Pyrolysis Gas Generated from Willow Wood. Processes 2023, 11, 2103. [Google Scholar] [CrossRef]
  50. Kukharets, S.; Jasinskas, A.; Golub, G.; Sukmaniuk, O.; Hutsol, T.; Mudryk, K.; Čėsna, J.; Glowacki, S.; Horetska, I. The Experimental Study of the Efficiency of the Gasification Process of the Fast-Growing Willow Biomass in a Downdraft Gasifier. Energies 2023, 16, 578. [Google Scholar] [CrossRef]
  51. Chen, D.; Li, Y.; Cen, K.; Luo, M.; Li, H.; Lu, B. Pyrolysis Polygeneration of Poplar Wood: Effect of Heating Rate and Pyrolysis Temperature. Bioresour. Technol. 2016, 218, 780–788. [Google Scholar] [CrossRef]
  52. Lakshman, V.; Brassard, P.; Hamelin, L.; Raghavan, V.; Godbout, S. Pyrolysis of Miscanthus: Developing the Mass Balance of a Biorefinery through Experimental Tests in an Auger Reactor. Bioresour. Technol. Rep. 2021, 14, 100687. [Google Scholar] [CrossRef]
  53. Azeta, O.; Ayeni, A.O.; Agboola, O.; Elehinafe, F.B. A Review on the Sustainable Energy Generation from the Pyrolysis of Coconut Biomass. Sci. Afr. 2021, 13, e00909. [Google Scholar] [CrossRef]
  54. Mohan, D.; Pittman, C.U.; Steele, P.H. Pyrolysis of Wood/Biomass for Bio-Oil: A Critical Review. Energy Fuels 2006, 20, 848–889. [Google Scholar] [CrossRef]
  55. Volpi, M.P.C.; Silva, J.C.G.; Hornung, A.; Ouadi, M. Review of the Current State of Pyrolysis and Biochar Utilization in Europe: A Scientific Perspective. Clean. Technol. 2024, 6, 152–175. [Google Scholar] [CrossRef]
  56. Ahmed, A.; Abu Bakar, M.S.; Sukri, R.S.; Hussain, M.; Farooq, A.; Moogi, S.; Park, Y.-K. Sawdust Pyrolysis from the Furniture Industry in an Auger Pyrolysis Reactor System for Biochar and Bio-Oil Production. Energy Convers. Manag. 2020, 226, 113502. [Google Scholar] [CrossRef]
  57. Irfan, M.; Chen, Q.; Yue, Y.; Pang, R.; Lin, Q.; Zhao, X.; Chen, H. Co-Production of Biochar, Bio-Oil and Syngas from Halophyte Grass (Achnatherum splendens L.) under Three Different Pyrolysis Temperatures. Bioresour. Technol. 2016, 211, 457–463. [Google Scholar] [CrossRef] [PubMed]
  58. Imam, T.; Capareda, S. Characterization of Bio-Oil, Syn-Gas and Bio-Char from Switchgrass Pyrolysis at Various Temperatures. J. Anal. Appl. Pyrolysis 2012, 93, 170–177. [Google Scholar] [CrossRef]
  59. Mahinpey, N.; Murugan, P.; Mani, T.; Raina, R. Analysis of Bio-Oil, Biogas, and Biochar from Pressurized Pyrolysis of Wheat Straw Using a Tubular Reactor. Energy Fuels 2009, 23, 2736–2742. [Google Scholar] [CrossRef]
  60. Chen, T.; Liu, R.; Scott, N.R. Characterization of Energy Carriers Obtained from the Pyrolysis of White Ash, Switchgrass and Corn Stover—Biochar, Syngas and Bio-Oil. Fuel Process. Technol. 2016, 142, 124–134. [Google Scholar] [CrossRef]
  61. Chojnacki, J.; Kielar, J.; Kukiełka, L.; Najser, T.; Pachuta, A.; Berner, B.; Zdanowicz, A.; Frantík, J.; Najser, J.; Peer, V. Batch Pyrolysis and Co-Pyrolysis of Beet Pulp and Wheat Straw. Materials 2022, 15, 1230. [Google Scholar] [CrossRef]
  62. Mishra, R.K.; Misra, Y.; Prasanna Kumar, D.J.; Sankannavar, R.; Kumar, P. Environmental Impacts on Second-Generation Biofuel Production from Lignocellulosic Biomass. In Biofuels Production from Lignocellulosic Materials; Elsevier: Amsterdam, The Netherlands, 2025; pp. 101–123. [Google Scholar]
  63. Salami, R.; Kordi, M.; Bolouri, P.; Delangiz, N.; Asgari Lajayer, B. Algae-Based Biorefinery as a Sustainable Renewable Resource. Circ. Econ. Sustain. 2021, 1, 1349–1365. [Google Scholar] [CrossRef]
  64. da Rosa, M.D.H.; Alves, C.J.; dos Santos, F.N.; de Souza, A.O.; da Rosa Zavareze, E.; Pinto, E.; Noseda, M.D.; Ramos, D.; de Pereira, C.M.P. Macroalgae and Microalgae Biomass as Feedstock for Products Applied to Bioenergy and Food Industry: A Brief Review. Energies 2023, 16, 1820. [Google Scholar] [CrossRef]
  65. De Bhowmick, G.; Sarmah, A.K.; Sen, R. Zero-Waste Algal Biorefinery for Bioenergy and Biochar: A Green Leap towards Achieving Energy and Environmental Sustainability. Sci. Total Environ. 2019, 650, 2467–2482. [Google Scholar] [CrossRef]
  66. Narayanan, M. Biorefinery Products from Algal Biomass by Advanced Biotechnological and Hydrothermal Liquefaction Approaches. Discov. Appl. Sci. 2024, 6, 146. [Google Scholar] [CrossRef]
  67. Moncada, J.; Tamayo, J.A.; Cardona, C.A. Integrating First, Second, and Third Generation Biorefineries: Incorporating Microalgae into the Sugarcane Biorefinery. Chem. Eng. Sci. 2014, 118, 126–140. [Google Scholar] [CrossRef]
  68. Moncada, J.; Cardona, C.A.; Rincón, L.E. Design and Analysis of a Second and Third Generation Biorefinery: The Case of Castorbean and Microalgae. Bioresour. Technol. 2015, 198, 836–843. [Google Scholar] [CrossRef]
  69. Gheewala, S.H. Life Cycle Assessment for Sustainability Assessment of Biofuels and Bioproducts. Biofuel Res. J. 2023, 10, 1810–1815. [Google Scholar] [CrossRef]
  70. Ayisha Naziba, T.; Praveen Kumar, D.; Karthikeyan, S.; Sriramajayam, S.; Djanaguiraman, M.; Sundaram, S.; Ghamari, M.; Prasada Rao, R.; Ramakrishna, S.; Ramesh, D. Biomass Derived Biofluorescent Carbon Dots for Energy Applications: Current Progress and Prospects. Chem. Rec. 2024, 24, e202400030. [Google Scholar] [CrossRef]
  71. Dhanya, M.S. Perspectives of Agro-Waste Biorefineries for Sustainable Biofuels. In Zero Waste Biorefinery; Springer Nature: Singapore, 2022; pp. 207–232. [Google Scholar]
  72. Ahmed, S.F.; Kabir, M.; Mehjabin, A.; Oishi, F.T.Z.; Ahmed, S.; Mannan, S.; Mofijur, M.; Almomani, F.; Badruddin, I.A.; Kamangar, S. Waste Biorefinery to Produce Renewable Energy: Bioconversion Process and Circular Bioeconomy. Energy Rep. 2023, 10, 3073–3091. [Google Scholar] [CrossRef]
  73. Ogwu, M.C.; Kosoe, E.A.; Osawaru, M.E. Raw Materials for Sustainable Bioeconomy Development in the Global South. In Sustainable Bioeconomy Development in the Global South; Springer Nature: Singapore, 2025; pp. 37–63. [Google Scholar]
  74. Makepa, D.C.; Chihobo, C.H. Barriers to Commercial Deployment of Biorefineries: A Multi-Faceted Review of Obstacles across the Innovation Chain. Heliyon 2024, 10, e32649. [Google Scholar] [CrossRef] [PubMed]
  75. Guajardo, N.; Schrebler, R.A. Upstream and Downstream Bioprocessing in Enzyme Technology. Pharmaceutics 2023, 16, 38. [Google Scholar] [CrossRef]
  76. Nleya, Y.; Young, B.; Nooraee, E.; Baroutian, S. Opportunities and Challenges for Anaerobic Digestion of Farm Dairy Effluent. ChemBioEng Rev. 2023, 10, 924–940. [Google Scholar] [CrossRef]
  77. Elsayed, A.; Laqa Kakar, F.; Mustafa Abdelrahman, A.; Ahmed, N.; AlSayed, A.; Sherif Zagloul, M.; Muller, C.; Bell, K.Y.; Santoro, D.; Norton, J.; et al. Enhancing Anaerobic Digestion Efficiency: A Comprehensive Review on Innovative Intensification Technologies. Energy Convers. Manag. 2024, 320, 118979. [Google Scholar] [CrossRef]
  78. Müller-Langer, F.; Majer, S.; O’Keeffe, S. Benchmarking Biofuels—A Comparison of Technical, Economic and Environmental Indicators. Energy Sustain. Soc. 2014, 4, 20. [Google Scholar] [CrossRef]
  79. Mazzanti, G.; Demichelis, F.; Fino, D.; Tommasi, T. A Closed-Loop Valorization of the Waste Biomass through Two-Stage Anaerobic Digestion and Digestate Exploitation. Renew. Sustain. Energy Rev. 2025, 207, 114938. [Google Scholar] [CrossRef]
  80. Decker, S.R.; Milbrandt, A. Anaerobic Digestion of Food Waste: Products and Their Uses. Available online: https://www.nrel.gov/docs/fy22osti/81676.pdf (accessed on 8 February 2025).
  81. Okolie, J.A.; Epelle, E.I.; Tabat, M.E.; Orivri, U.; Amenaghawon, A.N.; Okoye, P.U.; Gunes, B. Waste Biomass Valorization for the Production of Biofuels and Value-Added Products: A Comprehensive Review of Thermochemical, Biological and Integrated Processes. Process Saf. Environ. Prot. 2022, 159, 323–344. [Google Scholar] [CrossRef]
  82. Munir, M.T.; Mansouri, S.S.; Udugama, I.A.; Baroutian, S.; Gernaey, K.V.; Young, B.R. Resource Recovery from Organic Solid Waste Using Hydrothermal Processing: Opportunities and Challenges. Renew. Sustain. Energy Rev. 2018, 96, 64–75. [Google Scholar] [CrossRef]
  83. Kargbo, H.; Harris, J.S.; Phan, A.N. “Drop-in” Fuel Production from Biomass: Critical Review on Techno-Economic Feasibility and Sustainability. Renew. Sustain. Energy Rev. 2021, 135, 110168. [Google Scholar] [CrossRef]
  84. Brutyan, M.M. Foresight of Microalgae Usage for the Production of Third-Generation Biofuel. Indian. J. Sci. Technol. 2017, 10, 1–10. [Google Scholar] [CrossRef]
  85. Dębowski, M.; Świca, I.; Kazimierowicz, J.; Zieliński, M. Large Scale Microalgae Biofuel Technology—Development Perspectives in Light of the Barriers and Limitations. Energies 2022, 16, 81. [Google Scholar] [CrossRef]
  86. Al-Jabri, H.; Das, P.; Khan, S.; Thaher, M.; AbdulQuadir, M. Treatment of Wastewaters by Microalgae and the Potential Applications of the Produced Biomass—A Review. Water 2020, 13, 27. [Google Scholar] [CrossRef]
  87. Brown, A.; Ebadian, M.; Saddler, J.; Nylund, N.-O.; Aakko-Saksa, P.; Waldheim, L.; Bacovsky, D. The Role of Renewable Transport Fuels in Decarbonizing Road Transport. Available online: https://www.ieabioenergy.com/wp-content/uploads/2020/11/Production-Technologies-and-Costs.pdf (accessed on 8 February 2025).
  88. Srivastava, N.; Singh, R.; Singh, P.; Ahmad, I.; Singh, R.P.; Rai, A.K.; Asiri, M.; Gupta, V.K. Recent Advances on Lignocellulosic Bioresources and Their Valorization in Biofuels Production: Challenges and Viability Assessment. Environ. Technol. Innov. 2023, 29, 103037. [Google Scholar] [CrossRef]
  89. Ghamari, M.; Sun, D.; Dai, Y.; See, C.H.; Yu, H.; Edirisinghe, M.; Sundaram, S. Valorization of Diverse Waste-Derived Nanocellulose for Multifaceted Applications: A Review. Int. J. Biol. Macromol. 2024, 280, 136130. [Google Scholar] [CrossRef]
  90. El-Araby, R. Biofuel Production: Exploring Renewable Energy Solutions for a Greener Future. Biotechnol. Biofuels Bioprod. 2024, 17, 129. [Google Scholar] [CrossRef]
  91. Sventzouri, E.; Manthos, G.; Tsigkou, K.; Mastropetros, S.G.; Pispas, K.; Zagklis, D.; Ali, S.S.; Kornaros, M. Municipal Effluents: Generation, Characteristics, Impacts, and Applications for Bio-Based Product Recovery in a Biorefinery. In Biorefinery of Industrial Effluents for a Sustainable Circular Economy; Elsevier: Amsterdam, The Netherlands, 2025; pp. 95–110. [Google Scholar]
  92. Gitanjali, J.; Kalpana, M.; Ramesh, D.; Karthikeyan, S.; Venkatesa Palanichamy, N. Biofuel Potential Assignment Tool. Available online: https://drive.google.com/file/d/1qzHrWCJw4iqi3dhqy0AzwyU_wMsdo4kP/view (accessed on 8 February 2025).
  93. Guo, M.; Song, W.; Buhain, J. Bioenergy and Biofuels: History, Status, and Perspective. Renew. Sustain. Energy Rev. 2015, 42, 712–725. [Google Scholar] [CrossRef]
  94. Paul, S.; Panja, A.; Jha, P. Hindrances and Drawbacks of the Existing Policies and Roadmap for Sustainable Production of Biofuels: An Indian Scenario. In Biofuels and Sustainability; Elsevier: Amsterdam, The Netherlands, 2025; pp. 237–252. [Google Scholar]
  95. Patel, A.; Shah, A.R. Integrated Lignocellulosic Biorefinery: Gateway for Production of Second Generation Ethanol and Value Added Products. J. Bioresour. Bioprod. 2021, 6, 108–128. [Google Scholar] [CrossRef]
  96. Saravanan, A.P.; Mathimani, T.; Deviram, G.; Rajendran, K.; Pugazhendhi, A. Biofuel Policy in India: A Review of Policy Barriers in Sustainable Marketing of Biofuel. J. Clean. Prod. 2018, 193, 734–747. [Google Scholar] [CrossRef]
  97. Usmani, Z.; Sharma, M.; Awasthi, A.K.; Lukk, T.; Tuohy, M.G.; Gong, L.; Nguyen-Tri, P.; Goddard, A.D.; Bill, R.M.; Nayak, S.C.; et al. Lignocellulosic Biorefineries: The Current State of Challenges and Strategies for Efficient Commercialization. Renew. Sustain. Energy Rev. 2021, 148, 111258. [Google Scholar] [CrossRef]
  98. Kumar Biswas, P.; Pohit, S. What Ails India’s Biodiesel Programme? Energy Policy 2013, 52, 789–796. [Google Scholar] [CrossRef]
  99. Dutta, A.; Patra, A.; Hazra, K.K.; Nath, C.P.; Kumar, N.; Rakshit, A. A State of the Art Review in Crop Residue Burning in India: Previous Knowledge, Present Circumstances and Future Strategies. Environ. Chall. 2022, 8, 100581. [Google Scholar] [CrossRef]
  100. Kothari, R.; Vashishtha, A.; Singh, H.M.; Pathak, V.V.; Tyagi, V.V.; Yadav, B.C.; Ashokkumar, V.; Singh, D.P. Assessment of Indian Bioenergy Policy for Sustainable Environment and Its Impact for Rural India: Strategic Implementation and Challenges. Environ. Technol. Innov. 2020, 20, 101078. [Google Scholar] [CrossRef]
  101. Biogas: Converting Waste to the Best Renewable Energy Resource. Available online: https://www.peda.gov.in/waste-to-energy-projects (accessed on 25 February 2025).
  102. Haryana Bio-Energy Policy. 2018. Available online: https://hareda.gov.in/document/haryana-bio-energy-policy-2018 (accessed on 25 February 2025).
  103. Bio Energy Program. Available online: https://upneda.org.in/bio-energy-program.aspx (accessed on 25 February 2025).
  104. Rajasthan Integrated Clean Energy Policy. 2024. Available online: https://www.eqmagpro.com/wp-content/uploads/2024/12/Final-Draft_Itegrated-Clean-Energy-Policy2024-Nov24-VER1-1-final-1_compressed-1-28.pdf (accessed on 25 February 2025).
  105. Determination of Generic Tariff and Other Terms and Conditions for Procurement of Power by Distribution Licensees from Municipal Solid Waste to Energy Projects in the State of Gujarat. MSW Discussion Paper 2023. 2016. Available online: https://www.eqmagpro.com/determination-of-generic-tariff-and-other-terms-and-conditions-for-procurement-of-power-by-distributionlicensees-from-municipal-solid-wasteto-energy-projects-in-the-state-of-gujarat-eq/ (accessed on 25 February 2025).
  106. Madhya Pradesh Renewable Energy Policy—202. Available online: https://www.nsefi.in/assets/policies/Madhya_pradesh_renewable_enrgy_policy_2022.pdf (accessed on 25 February 2025).
  107. Study of Opportunities Associated with Biogas Energy in Jharkhand. Available online: https://www.researchgate.net/publication/352367485_Study_of_Opportunities_Associated_with_Biogas_Energy_in_Jharkhand (accessed on 25 February 2025).
  108. Sori, S.K.; Sushila, K.; Ekka, A. Economic Analysis of Biofuel Policy of Chhattisgarh. Available online: https://www.researchgate.net/publication/276252837_Economic_analysis_of_Biofuel_policy_of_Chhattisgarh (accessed on 25 February 2025).
  109. Biomass Energy. Available online: https://tgredco.telangana.gov.in/Biomass.aspx (accessed on 25 February 2025).
  110. Bio Energy and Solar Energy Programmes/Schemes. Available online: https://nredcap.in/BioEnergy_Solar_Programs.aspx (accessed on 25 February 2025).
  111. Kavya Koonampilli Policy and Market Briefing. 2024. Available online: https://www.worldbiogasassociation.org/wp-content/uploads/2024/10/WBA-India-Policy-and-Market-Briefing-2024.pdf (accessed on 13 March 2025).
  112. Ethanol Blending Policy. Available online: https://cms.tn.gov.in/cms_migrated/document/GO/ind_e_71_2023.pdf (accessed on 13 March 2025).
  113. Biomass (Agro-Waste) Based Power Project. Available online: https://www.mahaurja.com/meda/en/grid_connected_power/biomass (accessed on 25 February 2025).
  114. RE Programs. Available online: https://oredaodisha.com/re-programs/ (accessed on 25 February 2025).
  115. Bio Energy Programme. Available online: http://www.wbreda.org/bio-energy-programme/ (accessed on 25 February 2025).
  116. Unnat Chullha Abhiyan Programme. Available online: https://krishijagran.com/agriculture-world/tripura-s-bio-villages-aim-to-offer-sustainable-livelihood-opportunities-deputy-cm/ (accessed on 25 February 2025).
  117. Biogas. Available online: https://sikkimsreda.in/BioGas.html (accessed on 25 February 2025).
  118. Projects & Activities. Available online: https://nre.nagaland.gov.in/ (accessed on 25 February 2025).
  119. Meghalaya Power Policy. Available online: https://www.mnreda.gov.in/index.htm (accessed on 25 February 2025).
  120. National Biogas Development Project. Available online: https://keralaagriculture.gov.in/en/2021/09/14/national-biogas-development-project (accessed on 25 February 2025).
  121. Biomass Gasification. Available online: https://aeda.assam.gov.in/frontimpotentdata/biomass-gasification (accessed on 25 February 2025).
  122. State of Environment Report for Chandigarh UT-2021. Available online: https://chandigarhenvis.gov.in/sites/default/files/pdffiles/SoER_Chandigrah%202021-5.pdf (accessed on 25 February 2025).
  123. Purohit, P.; Dhar, S. Lignocellulosic Biofuels in India: Current Perspectives, Potential Issues and Future Prospects. AIMS Energy 2018, 6, 453–486. [Google Scholar] [CrossRef]
  124. Grangeia, C.; Santos, L.; Lazaro, L.L.B. The Brazilian Biofuel Policy (RenovaBio) and Its Uncertainties: An Assessment of Technical, Socioeconomic and Institutional Aspects. Energy Convers. Manag. X 2022, 13, 100156. [Google Scholar] [CrossRef]
  125. Goswami, L.; Kayalvizhi, R.; Dikshit, P.K.; Sherpa, K.C.; Roy, S.; Kushwaha, A.; Kim, B.S.; Banerjee, R.; Jacob, S.; Rajak, R.C. A Critical Review on Prospects of Bio-Refinery Products from Second and Third Generation Biomasses. Chem. Eng. J. 2022, 448, 137677. [Google Scholar] [CrossRef]
  126. Singh Yadav, A.; Singh, P.; Sahu, R.; Thangamuthu, P.; Shyam Narain, R.; Anupam Rao, Y.; Balu, A.; Prasad Panda, B.; Sharma, A. Potential Utilization of Turpentine Oil as an Alternative Fuel. Mater. Today Proc. 2022, 63, A1–A8. [Google Scholar] [CrossRef]
  127. Chauhan, A.; Upadhyay, S.; Saini, G.; Senthilkumar, N. Agricultural Crop Residue Based Biomass in India: Potential Assessment, Methodology and Key Issues. Sustain. Energy Technol. Assess. 2022, 53, 102552. [Google Scholar] [CrossRef]
  128. Pattnaik, F.; Patra, B.R.; Nanda, S.; Mohanty, M.K.; Dalai, A.K.; Rawat, J. Drivers and Barriers in the Production and Utilization of Second-Generation Bioethanol in India. Recycling 2024, 9, 19. [Google Scholar] [CrossRef]
  129. Chatterjee, E. India’s Oligarchic State Capitalism. Curr. Hist. 2023, 122, 123–130. [Google Scholar] [CrossRef]
  130. Sukumaran, R.K.; Mathew, A.K.; Kiran Kumar, M.; Abraham, A.; Chistopher, M.; Sankar, M. First- and Second-Generation Ethanol in India: A Comprehensive Overview on Feedstock Availability, Composition, and Potential Conversion Yields. In Sustainable Biofuels Development in India; Springer International Publishing: Cham, Switzerland, 2017; pp. 223–246. [Google Scholar]
  131. Duarah, P.; Haldar, D.; Patel, A.K.; Dong, C.-D.; Singhania, R.R.; Purkait, M.K. A Review on Global Perspectives of Sustainable Development in Bioenergy Generation. Bioresour. Technol. 2022, 348, 126791. [Google Scholar] [CrossRef]
  132. Purohit, P.; Dhar, S. Biofuel Roadmap for India; UNEP DTU Partnership: New Delhi, India, 2015. [Google Scholar]
  133. Singal, S.K. Review of Augmentation of Energy Needs Using Renewable Energy Sources in India. Renew. Sustain. Energy Rev. 2007, 11, 1607–1615. [Google Scholar] [CrossRef]
  134. Murphy, F.; Sosa, A.; McDonnell, K.; Devlin, G. Life Cycle Assessment of Biomass-to-Energy Systems in Ireland Modelled with Biomass Supply Chain Optimisation Based on Greenhouse Gas Emission Reduction. Energy 2016, 109, 1040–1055. [Google Scholar] [CrossRef]
  135. Yu, S.; Tao, J. Economic, Energy and Environmental Evaluations of Biomass-Based Fuel Ethanol Projects Based on Life Cycle Assessment and Simulation. Appl. Energy 2009, 86, S178–S188. [Google Scholar] [CrossRef]
  136. Giarola, S.; Zamboni, A.; Bezzo, F. Spatially Explicit Multi-Objective Optimisation for Design and Planning of Hybrid First and Second Generation Biorefineries. Comput. Chem. Eng. 2011, 35, 1782–1797. [Google Scholar] [CrossRef]
  137. Tsiropoulos, I.; Faaij, A.P.C.; Lundquist, L.; Schenker, U.; Briois, J.F.; Patel, M.K. Life Cycle Impact Assessment of Bio-Based Plastics from Sugarcane Ethanol. J. Clean. Prod. 2015, 90, 114–127. [Google Scholar] [CrossRef]
  138. Okoko, A.; Reinhard, J.; von Dach, S.W.; Zah, R.; Kiteme, B.; Owuor, S.; Ehrensperger, A. The Carbon Footprints of Alternative Value Chains for Biomass Energy for Cooking in Kenya and Tanzania. Sustain. Energy Technol. Assess. 2017, 22, 124–133. [Google Scholar] [CrossRef]
  139. Rajesh Banu, J.; Kavitha, S.; Yukesh Kannah, R.; Poornima Devi, T.; Gunasekaran, M.; Kim, S.-H.; Kumar, G. A Review on Biopolymer Production via Lignin Valorization. Bioresour. Technol. 2019, 290, 121790. [Google Scholar] [CrossRef]
  140. Özdenkçi, K.; De Blasio, C.; Muddassar, H.R.; Melin, K.; Oinas, P.; Koskinen, J.; Sarwar, G.; Järvinen, M. A Novel Biorefinery Integration Concept for Lignocellulosic Biomass. Energy Convers. Manag. 2017, 149, 974–987. [Google Scholar] [CrossRef]
  141. Awasthi, M.K.; Sarsaiya, S.; Patel, A.; Juneja, A.; Singh, R.P.; Yan, B.; Awasthi, S.K.; Jain, A.; Liu, T.; Duan, Y.; et al. Refining Biomass Residues for Sustainable Energy and Bio-Products: An Assessment of Technology, Its Importance, and Strategic Applications in Circular Bio-Economy. Renew. Sustain. Energy Rev. 2020, 127, 109876. [Google Scholar] [CrossRef]
  142. Adom, F.; Dunn, J.B.; Han, J.; Sather, N. Life-Cycle Fossil Energy Consumption and Greenhouse Gas Emissions of Bioderived Chemicals and Their Conventional Counterparts. Environ. Sci. Technol. 2014, 48, 14624–14631. [Google Scholar] [CrossRef]
  143. Singh, N.; Singhania, R.R.; Nigam, P.S.; Dong, C.-D.; Patel, A.K.; Puri, M. Global Status of Lignocellulosic Biorefinery: Challenges and Perspectives. Bioresour. Technol. 2022, 344, 126415. [Google Scholar] [CrossRef] [PubMed]
  144. Luo, L.; van der Voet, E.; Huppes, G. Biorefining of Lignocellulosic Feedstock—Technical, Economic and Environmental Considerations. Bioresour. Technol. 2010, 101, 5023–5032. [Google Scholar] [CrossRef] [PubMed]
  145. Kapoor, R.; Ghosh, P.; Kumar, M.; Sengupta, S.; Gupta, A.; Kumar, S.S.; Vijay, V.; Kumar, V.; Kumar Vijay, V.; Pant, D. Valorization of Agricultural Waste for Biogas Based Circular Economy in India: A Research Outlook. Bioresour. Technol. 2020, 304, 123036. [Google Scholar] [CrossRef] [PubMed]
  146. Cazzola, P.; Morrison, G.; Kaneko, H.; Cuenot, F.; Ghandi, A.; Fulton, L. Production Costs of Alternative Transport Fuels: Influence of Crude Oil Price and Technology Maturity; IEA: Paris, France, 2013. [Google Scholar]
Figure 1. Biorefinery approach to biomass valorization.
Figure 1. Biorefinery approach to biomass valorization.
Biomass 05 00016 g001
Figure 2. Management of renewable energy flows within a circular economy [125].
Figure 2. Management of renewable energy flows within a circular economy [125].
Biomass 05 00016 g002
Table 3. Energy generation potential and bioproducts from various biomass [92].
Table 3. Energy generation potential and bioproducts from various biomass [92].
BiomassPropertiesTechnologyEstimated Energy Generation PotentialBioproducts
Crop residuesCrop straws (Paddy straw, wheat straw, barley straw)Cellulose, %: 30–45
Hemicellulose, %: 20–25
Lignin, %: 10–20
Ash content, %: 4–20
Moisture, %: 8–12
Energy value, MJ/kg: 10–16
Bulk density, kg/m3: 50–120
Anaerobic digestionBiogas: 0.3–0.6 m3 per kg volatile solidsBio-digestate slurry
FermentationBioethanol: 0.3–0.5 L per kg dry biomassBiocompost, animal feed, biochemicals
PyrolysisBiooil: 0.2–0.3 L per kg dry biomass
Biochar: 0.2–0.25 kg per kg dry biomass
Pyrogas
GasificationSyngas: 1–1.5 m3 per kg dry biomassBiochar
HTC/HTLBiocrude: 0.3–0.5 L per kg dry biomass
Hydrochar: 0.3–0.4 kg per kg dry biomass
Aqueous phase
Crop stalks
(cotton stalk, millet stalk, corn stalk, pea stalk)
Cellulose, %: 30–45
Hemicellulose, %: 15–30
Lignin, %: 10–25
Ash content, %: 3–8
Moisture, %: 8–14
Energy value, MJ/kg: 14–18
Bulk density, kg/m3: 50–150
Anaerobic digestionBiogas: 0.3–0.7 m3 per kg volatile solidsBio-digestate slurry
FermentationBioethanol: 0.25–0.45 L per kg dry biomassAnimal feed, organic acids, biochemicals
PyrolysisBiooil: 0.2–0.35 L per kg dry biomass
Biochar: 0.25–0.3 kg per kg dry biomass
Pyrogas
GasificationSyngas: 1–1.5 m3 per kg dry biomassBiochar
HTC/HTLBiocrude: 0.3–0.5 L per kg dry biomass
Hydrochar: 0.3–0.5 kg per kg dry biomass
Aqueous phase
Agro Processing ResiduesHusks and Shells
(Coconut, sunflower, coffee, paddy husks and nut shell)
Cellulose, %: 25–45
Hemicellulose, %: 15–25
Lignin, %: 15–45
Ash content, %: 0.5–5
Moisture, %: 5–15
Energy value, MJ/kg: 13–20
Bulk density, kg/m3: 80–400
Anaerobic digestionBiogas: 0.2–0.4 m3 per kg volatile solidsBio-digestate slurry
FermentationBioethanol: 0.1–0.25 L per kg dry biomassStillage, animal feed
PyrolysisBiooil: 0.3–0.5 L per kg dry biomass
Biochar: 0.25–0.35 kg per kg dry biomass
Pyrogas
GasificationSyngas: 1–1.5 m3 per kg dry biomassBiochar
HTC/HTLBiocrude: 0.4–0.6 L per kg dry biomass
Hydrochar: 0.3–0.5 kg per kg dry biomass
Aqueous phase
Fruit and Vegetable Waste (Peels, pomace, seeds)Carbohydrates, %: 20–40
Lipids, %: 2–40
Ash content, %: 2–8
Moisture, %: 10–90
Energy value, MJ/kg: 10–25
Bulk density, kg/m3: 250–800
Anaerobic digestionBiogas: 0.2–0.4 m3 per kg volatile solidsBio-digestate
FermentationBioethanol: 0.1–0.25 L per kg dry biomassBio-composites, biopolymers
PyrolysisBiooil: 0.3–0.5 L per kg dry biomass
Biochar: 0.25–0.35 kg per kg dry biomass
Pyrogas
GasificationSyngas: 1–1.5 m3 per kg dry biomassBiochar
HTC/HTLBiocrude: 0.3–0.5 L per kg dry biomass
Hydrochar: 0.4–0.6 kg per kg dry biomass
Bioactive compounds
Oil industry (Fruit bunches, fronds, oil cake)Lignin, %: 5–25
Ash content, %: 4–20
Moisture, %: 12–60
Energy value, MJ/kg: 14–20
Bulk density, kg/m3: 100–600
Anaerobic digestionBiogas: 0.3–0.5 m3 per kg volatile solidsbio-compost, bio-digestate
FermentationBioethanol: 0.1–0.25 L per kg dry biomassBioplastic, animal feed
PyrolysisBiooil: 0.3–0.6 L per kg dry biomass
Biochar: 0.2–0.35 kg per kg dry biomass
Pyrogas
GasificationSyngas: 1–1.5 m3 per kg dry biomassBiochar
HTC/HTLBiocrude: 0.3–0.5 L per kg dry biomass
Hydrochar: 0.3–0.6 kg per kg dry biomass
Phenols, biochemicals
Brewery and Distillery Waste (Spent grain, distiller’s dried grains)Cellulose, %: 17–30
Hemicellulose, %: 15–35
Lignin, %: 10–18
Lipids, %: 5–12
Moisture, %db: 8–12
Moisture, %wb: 70–80
Energy value, MJ/kg: 10–12
Bulk density, kg/m3: 200–300
Anaerobic digestionBiogas: 0.3–0.5 m3 per kg volatile solidsBio-digestate
FermentationBioethanol: 0.1–0.25 L per kg dry biomassBiocompost
PyrolysisBiooil: 0.3–0.5 L per kg dry biomass
Biochar: 0.2–0.4 kg per kg dry biomass
Animal feed
GasificationSyngas: 1–1.5 m3 per kg dry biomassBiochar
HTC/HTLBiocrude: 0.3–0.5 L per kg dry biomass
Hydrochar: 0.3–0.5 kg per kg dry biomass
Biochemicals, phenols
Energy CropsPerennial Grasses (Switchgrass, miscanthus, Napier grass)Cellulose, %: 30–50
Hemicellulose, %: 20–30
Lignin, %: 10–25
Ash content, %: 1–8
Moisture, %: 10–20
Energy value, MJ/kg: 15–19
Bulk density, kg/m3: 50–150
Anaerobic digestionBiogas: 0.3–0.5 m3 per kg volatile solidsOrganic acids, Bio-digestate
FermentationBioethanol: 0.2–0.35 L per kg dry biomassBiocompost
PyrolysisBiooil: 0.2–0.4 L per kg dry biomass
Biochar: 0.2–0.3 kg per kg dry biomass
Pyrogas
GasificationSyngas: 1–1.5 m3 per kg dry biomassBiochar
HTC/HTLBiocrude: 0.2–0.4 L per kg dry biomass
Hydrochar: 0.4–0.6 kg per kg dry biomass
Biochemicals, nutrients
Woody Crops (Willow, Casuarina, eucalyptus)Cellulose, %: 40–50
Hemicellulose, %: 25–30
Lignin, %: 20–30
Ash content, %: 0.5–3
Moisture, %: 10–15
Energy value, MJ/kg: 17–20
Bulk density, kg/m3: 180–350
Anaerobic digestionBiogas: 0.2–0.4 m3 per kg volatile solidsBio-digestate
FermentationBioethanol: 0.15–0.25 L per kg dry biomassPharmaceuticals
PyrolysisBiooil: 0.2–0.4 L per kg dry biomass
Biochar: 0.3–0.4 kg per kg dry biomass
Aromatic oils, pyrogas
GasificationSyngas: 1–1.5 m3 per kg dry biomassBiochar
HTC/HTLBiocrude: 0.2–0.4 L per kg dry biomass
Hydrochar: 0.4–0.6 kg per kg dry biomass
Liquid fertilizer
Non-edible plant (jatropha)Cellulose, %: 35–45
Hemicellulose, %: 20–30
Lignin, %: 25–35
Ash content, %: 4–10
Moisture, %: 8–14
Energy value, MJ/kg: 18–22
Bulk density, kg/m3: 200–300
Anaerobic digestionBiogas: 0.3–0.5 m3 per kg volatile solidsBio-digestate
FermentationBioethanol: 0.12–0.20 L per kg dry biomassBioplastics
PyrolysisBiooil: 0.2–0.4 L per kg dry biomass
Biochar: 0.3–0.4 kg per kg dry biomass
Pyrogas
GasificationSyngas: 1–1.5 m3 per kg dry biomassBiochar
HTC/HTLBiocrude: 0.2–0.4 L per kg dry biomass
Hydrochar: 0.4–0.5 kg per kg dry biomass
Nutraceuticals, biochemicals
Aquatic biomassAlgae (microalgae and macroalgae)Cellulose, %: 10–20
Hemicellulose, %: 5–15
Lignin, %: <1
Ash content, %: 10–40
Moisture, %wb: 80–90
Moisture, %db: 10–20
Energy value, MJ/kg: 10–25
Bulk density, kg/m3: 100–300
Anaerobic digestionBiogas: 0.2–0.4 m3 per kg of biomassBio-digestate
FermentationBioethanol: 0.1–0.2 L per kg biomassbioplastics
PyrolysisBiooil: 0.1–0.3 L per kg biomass
Biochar: 0.2–0.3 kg per kg biomass
Nutraceuticals
GasificationSyngas: 1–1.5 m3 per kg biomassBiochar
HTC/HTLBiocrude: 0.3–0.5 L per kg biomass
Hydrochar: 0.3–0.5 kg per kg biomass
Nutrient recover, chemicals
Water hyacinth and duckweed (aquatic plants)Cellulose, %: 15–40
Hemicellulose, %: 10–30
Lignin, %: 1–20
Ash content, %: 10–25
Moisture, %wb: 80–95
Moisture, %db: 5–20
Energy value, MJ/kg: 10–18
Bulk density, kg/m3: 80–250
Anaerobic digestionBiogas: 0.2–0.4 m3 per kg of biomassBio-digestate
FermentationBioethanol: 0.1–0.2 L per kg biomassOrganic acids
PyrolysisBiooil: 0.1–0.3 L per kg biomass
Biochar: 0.2–0.3 kg per kg biomass
Pyrogas, biochemicals
GasificationSyngas: 1–1.5 m3 per kg biomassBiochar
HTC/HTLBiocrude: 0.3–0.6 L per kg biomass
Hydrochar: 0.3–0.5 kg per kg biomass
Biochemicals, nutrients
Table 5. Environmental Benefits of Second-Generation Biorefineries.
Table 5. Environmental Benefits of Second-Generation Biorefineries.
Environmental ImpactDescription
Reduction in GHG EmissionsLignocellulosic biofuels approach carbon neutrality, offsetting CO2 emissions through plant sequestration.
Waste ValorizationUtilization of agricultural residues prevents open field burning, mitigating air pollution.
Biodiversity ConservationSustainable biomass sourcing reduces the need for agricultural land expansion, limiting deforestation.
Water ConservationAdvanced biorefineries consume 30–70% less water compared to first-generation biofuels; water recycling systems improve efficiency.
Soil Health ImprovementBy-products such as biochar and bio-digestate enhance soil carbon content and microbial activity, improving agricultural sustainability.
Table 6. Economic Benefits of Second-Generation Biorefineries.
Table 6. Economic Benefits of Second-Generation Biorefineries.
Economy ImpactDescription
Reduced Fossil Fuel DependencyDomestic biofuel production reduces crude oil imports, strengthening trade balance and energy security.
Market GrowthIndia‘s bioethanol market is projected to grow at a CAGR of 8.7%, potentially doubling by 2030.
Investment AttractionMajor corporations like Reliance and Adani Group have committed substantial investments in bioenergy.
Value-Added ProductsBiorefineries produce high-value chemicals such as xylitol, furfural, and organic acids, enhancing profitability.
Rural DevelopmentIncreased demand for agricultural residues boosts rural incomes and stimulates local supply chains.
Table 7. Energy Benefits of Second-Generation Biorefineries.
Table 7. Energy Benefits of Second-Generation Biorefineries.
Economy ImpactDescription
Energy Demand GrowthEnergy demand rose from 6101 Mtoe (1973) to 13,699 Mtoe (2016).
GHG Emissions ReductionPotential 2.7% reduction in GDP by 2030 from second-generation biorefineries.
Solar Energy PotentialIndia’s annual solar potential exceeds 5000 trillion kWh.
CHP EfficiencyCHP systems in biorefineries achieve 80–90% efficiency, compared to 30–40% for conventional systems.
Renewable Energy ContributionIncreased demand for agricultural residues boosts rural incomes and stimulates local supply chains.
Energy DiversificationBiomass diversifies India’s energy portfolio, reducing reliance on fossil fuels.
Decentralized Energy ProductionBiorefineries contribute to rural electrification by reducing transmission losses.
Integration with Other RenewablesCombines solar with biomass to address intermittency and optimize solar potential.
Grid StabilityBiogas and biomethane enhance grid stability, supporting renewable energy integration.
Transportation CostsTransportation can reduce biorefinery operational expenses.
Table 8. Key Parameters of LCA and Circular Economy Integration in India’s Biorefinery Sector.
Table 8. Key Parameters of LCA and Circular Economy Integration in India’s Biorefinery Sector.
ParameterDetails
Carbon Footprint ReductionBio-derived polyethylene reduces emissions by 0.75 kg CO2-eq/kg compared to fossil-based polyethylene.
Process OptimizationCharcoal value chain emissions reduced from 2.15 CO2-eq to 0.50 CO2-eq through process improvements.
Circular Economy Resource Efficiency Circular biorefineries demonstrate near-zero waste and enhanced resource use through cascading biomass.
Environmental Performance of Circular EconomyCircular approaches reduce GHG emissions by 39–86% and non-renewable energy by 65% compared to linear models.
Economic Value CreationLignin valorization for polymers, bio-composites, and nanomaterials, with a market projected at USD 1.2 billion by 2025.
Sustainability AlignmentCircular economy principles support environmental, economic, and social sustainability goals, aligned with the UN SDGs.
Disclaimer/Publisher’s Note: The statements, opinions and data contained in all publications are solely those of the individual author(s) and contributor(s) and not of MDPI and/or the editor(s). MDPI and/or the editor(s) disclaim responsibility for any injury to people or property resulting from any ideas, methods, instructions or products referred to in the content.

Share and Cite

MDPI and ACS Style

Thaha, A.N.; Ghamari, M.; Jothiprakash, G.; Velusamy, S.; Karthikeyan, S.; Ramesh, D.; Sundaram, S. High Impact Biomass Valorization for Second Generation Biorefineries in India: Recent Developments and Future Strategies for Sustainable Circular Economy. Biomass 2025, 5, 16. https://doi.org/10.3390/biomass5010016

AMA Style

Thaha AN, Ghamari M, Jothiprakash G, Velusamy S, Karthikeyan S, Ramesh D, Sundaram S. High Impact Biomass Valorization for Second Generation Biorefineries in India: Recent Developments and Future Strategies for Sustainable Circular Economy. Biomass. 2025; 5(1):16. https://doi.org/10.3390/biomass5010016

Chicago/Turabian Style

Thaha, Ayisha Naziba, Mehrdad Ghamari, Gitanjali Jothiprakash, Sasireka Velusamy, Subburamu Karthikeyan, Desikan Ramesh, and Senthilarasu Sundaram. 2025. "High Impact Biomass Valorization for Second Generation Biorefineries in India: Recent Developments and Future Strategies for Sustainable Circular Economy" Biomass 5, no. 1: 16. https://doi.org/10.3390/biomass5010016

APA Style

Thaha, A. N., Ghamari, M., Jothiprakash, G., Velusamy, S., Karthikeyan, S., Ramesh, D., & Sundaram, S. (2025). High Impact Biomass Valorization for Second Generation Biorefineries in India: Recent Developments and Future Strategies for Sustainable Circular Economy. Biomass, 5(1), 16. https://doi.org/10.3390/biomass5010016

Article Metrics

Back to TopTop