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AFR can provide economic and environmental benefits

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Tushar Khandhadia, General Manager – Production, Udaipur Cement Works, in conversation with Kanika Mathur about the impact of AFR on efficiency and quality.

As the cement industry moves towardmore sustainable practices, alternative fuels and raw materials (AFR) play a crucial role in reducing carbon emissions and enhancing resource efficiency. In this exclusive interview, Tushar Khandhadia, General Manager – Production at Udaipur Cement Works, shares insights on how the company integrates AFR into its production process, the challenges involved, and the latest innovations driving sustainable cement manufacturing.

Which AFR does your company currently use in cement production?
Our organisation employs a variety of AFR to enhance sustainability and reduce our carbon footprint. These include:

  • Alternative fuels: Waste-derived fuels such as municipal solid waste (MSW), tire-derived fuel (TDF), biomass, and industrial waste, waste mix for co-incineration LCV.
  • Alternative raw materials: Industrial by-products like fly ash, f.f slag, jarosite chemical gypsum, granulated slag, bf dust, chemical sludge (waste water treatment, ETP sludge – solid, spent carbon, waste mix (solid)).

How do alternative fuels impact the efficiency and quality of cement?
While alternative fuels can provide economic and environmental benefits, they must be carefully managed to ensure that the final quality of the cement is not compromised. The key to optimising the impact of alternative fuels on cement production lies in the selection of the right types of fuels, proper blending, and controlling combustion conditions to maintain both efficiency and high-quality output.

Fuel characteristics

  • Energy content: Alternative fuels (such as biomass, waste-derived fuels, or industrial by-products) often have lower energy content compared to traditional fuels like coal or pet coke. This means that more of the alternative fuel is required to achieve the same level of heat generation. As a result, more fuel needs to be burned, potentially increasing the overall heat consumption of
    the kiln.
  • Moisture and volatile matter: Some alternative fuels have higher moisture content or volatile substances, requiring additional energy to evaporate the moisture or combust these volatile compounds. This can lead to a higher heat consumption during the combustion process.
  • Burning efficiency: combustion characteristics: Different alternative fuels may burn at different rates or temperatures compared to traditional fuels, which could affect the kiln’s efficiency. Incomplete combustion of some alternative fuels might cause heat losses and thus increase the energy needed to maintain kiln operation.
  • Clinker formation: Alternative fuels may affect the formation of clinker (the solid material produced in the kiln). If the composition or combustion characteristics of the alternative fuel cause uneven heating or changes in clinker quality, additional energy may be needed to stabilise the temperature or improve the quality of the clinker.
  • Operational adjustments: process optimisation: When switching to alternative fuels, adjustments are often required to optimise the kiln’s operational parameters (like air flow, temperature control, etc.). Until these adjustments are fully optimised, the kiln may operate less efficiently, leading to higher heat consumption.

Impact on quality:

  • Chemical composition: Some alternative fuels, such as those derived from industrial waste or hazardous materials, may introduce chemical compounds that can alter the final properties of cement. However, proper fuel management ensures that any potential adverse effects on cement quality are minimised.
  • Clinker quality: The quality of the clinker, which is the key ingredient in cement, can be affected by the composition of the alternative fuels. Some alternative fuels may introduce impurities (such as chlorine or sulphur), which could lead to clinker quality issues, such as instability or the formation of undesirable compounds.
  • Consistency in product: The use of alternative fuels can cause variations in the combustion process, which may lead to slight fluctuations in temperature and material composition. These inconsistencies could impact the final cement quality, though careful fuel selection and blending can mitigate these risks.
  • Environmental impacts on quality: One of the advantages of using alternative fuels is their potential to reduce the carbon footprint of cement production. The reduction of CO2 emissions and other pollutants indirectly benefits the overall quality of the end product, as it promotes sustainability and cleaner production processes.

Environmental and sustainability considerations

  • Lower CO2 emissions: By using alternative fuels, the cement industry can reduce its reliance on fossil fuels, thereby decreasing CO2 emissions. The use of waste materials like municipal solid waste or biomass can result in a carbon-neutral or lower-carbon cement production process.
  • Waste reduction: AFR helps recycle waste materials, reduce landfill use and promote circular economy practices, which indirectly enhances the sustainability of the cement industry.

What challenges do you face in sourcing and utilising AFR?
Sourcing and utilising AFR in cement production comes with several challenges that must be addressed to ensure that the transition is both effective and sustainable. Below are the key challenges typically faced:

Fuel quality variability

  • Inconsistent properties: AFRs such as waste materials, biomass or industrial by-products can vary significantly in their chemical composition, energy content, moisture levels and combustion characteristics. This inconsistency can complicate kiln operations, as cement plants are optimised for burning specific fuels like coal or petcoke. Variability in AFR can lead to issues with combustion efficiency, temperature control, and process stability.
  • Contaminants: Some AFRs may contain unwanted contaminants (e.g., plastics, heavy metals, chlorine, or sulfur) that could affect both the kiln’s performance and the quality of the final product. These contaminants can increase emissions or cause equipment corrosion and premature wear.

Supply chain and availability

  • Logistical complexity: Sourcing AFR requires a robust and reliable supply chain, as many alternative fuels come from waste streams that may not be consistently available. This variability in supply can lead to fluctuations in fuel availability, which may impact production schedules.
  • Sourcing reliability: The availability of certain types of AFRs may be limited by geographic location, government regulations, or competing demands (e.g., the use of biomass for other industries or energy production). This can make it difficult to secure a stable and consistent supply of AFR, particularly in regions where waste recycling infrastructure is underdeveloped.

Storage and handling

  • Storage issues: Some AFRs, especially organic or biomass-based fuels, may require specialised storage facilities to prevent degradation, moisture absorption, or contamination. Proper storage is necessary to maintain fuel quality and prevent losses due to spoilage.
  • Handling challenges: Different AFRs require different handling techniques, such as shredding, drying or sorting, before they can be used in the kiln. This adds complexity to the operational process and may require investment in new infrastructure and equipment.

Regulatory and environmental concerns

  • Compliance with regulations: The use of certain AFRs may be subject to stringent environmental regulations, particularly regarding emissions, waste management and fuel quality standards. Compliance with these regulations may require additional monitoring, testing and reporting, increasing operational costs and complexity.
  • Emission control: Some alternative fuels may lead to higher levels of certain pollutants (e.g., dioxins, furans, or particulate matter) if not properly managed. Cement plants must invest in additional air pollution control technologies (e.g., scrubbers, electrostatic precipitators) to mitigate these emissions.

Technical adaptation of kilns and equipment

  • Modification of existing systems: Cement plants may need to retrofit or upgrade their existing equipment (e.g., burners, air systems, or fuel handling systems) to efficiently utilise AFR. These modifications can be costly, time-consuming, and may require downtime.
  • Impact on kiln efficiency: The combustion characteristics of AFR differ from those of traditional fuels, and improper adaptation can lead to inefficient burning, lower kiln temperatures and lower overall kiln throughput. Continuous monitoring and optimisation of the kiln operation are essential to ensure efficient use of AFR.

Cost and economic viability

  • Initial investment: While AFRs can provide cost savings in the long term (especially if they are locally sourced or cheaper than conventional fuels), the upfront cost of modifying equipment, establishing fuel handling processes, and meeting regulatory requirements can be significant.
  • Price fluctuations: The cost of alternative fuels can fluctuate based on market conditions, waste availability, and local competition for resources. Such variability in pricing may make it difficult to predict savings over time and could affect the economic feasibility of using AFRs.

Quality control of cement

  • Impact on product consistency: The chemical composition of AFRs can affect the clinker quality and, in turn, the final cement product. Variations in the AFR may result in inconsistent burning conditions in the kiln, which can lead to variations in clinker mineral composition and final cement properties.
  • Blending and optimisation: To ensure that product quality remains consistent, cement producers must carefully manage the blending of alternative fuels with traditional fuels. Finding the right balance and ensuring stable quality control requires detailed analysis and optimisation.

Public perception and social acceptance

  • Concerns about waste incineration: In some regions, the use of waste-derived fuels in cement kilns may face resistance due to public concerns about the environmental and health impacts of burning waste. These concerns can affect the social acceptance of AFR use, particularly if local communities are not fully educated about the benefits of AFR in reducing waste and emissions.
  • Brand reputation: Cement companies must also be mindful of their brand reputation when using waste-derived fuels. Public perception can play a significant role in the company’s market standing, especially in more environmentally conscious regions.

Long-term sustainability of AFR supply

  • Sustainability of fuel sources: The long-term availability of certain types of AFR, such as biomass or waste-derived fuels, may be subject to factors like changing waste management practices, government policies, and market demand. Over-reliance on a single source of AFR could lead to supply chain disruptions or sustainability concerns in the future.

Strategies to overcome these challenges
To overcome these challenges, cement producers often adopt several strategies:

  • Diversification of AFR sources: Relying on a mix of different AFR types (e.g., industrial by-products, biomass, municipal waste) can help mitigate supply risks and fuel quality issues.
  • Partnerships and collaboration: Collaborating with waste management companies, municipalities, and regulatory bodies can help secure a reliable AFR supply and ensure compliance with regulations.
  • Technology and monitoring: Investing in advanced combustion technologies, sensors, and control systems can help optimise AFR utilisation in the kiln, ensuring efficient combustion and minimising emissions.
  • Training and skill development: Ensuring that staff are well-trained in handling and utilising AFRs can help minimise operational challenges and improve overall kiln efficiency.

While there are many challenges associated with sourcing and utilising AFR, many of them can be addressed with proper planning, technology, and management. The long-term benefits of using alternative fuels, including environmental sustainability and cost savings, often outweigh the challenges, especially with ongoing improvements in fuel handling and kiln optimisation.

How does AFR adoption contribute to cost savings and sustainability?
The adoption of AFR) in cement production can significantly contribute to both cost savings and sustainability. Here’s how:

Cost Savings

  • Reduced reliance on expensive fossil fuels: Traditional fuels like coal or petcoke can be subject to volatile price fluctuations due to geopolitical factors or market changes. AFRs, such as industrial by-products, biomass, or waste materials, are often less expensive than conventional fuels. By switching to AFRs, cement producers can lower their overall fuel costs.
  • Utilising waste streams: Many AFRs are waste products from other industries or municipal waste. Using these materials instead of purchasing new fuels reduces the cost of sourcing energy, as companies may even receive subsidies or payments for taking certain waste materials off their hands (e.g., biomass, plastics, tires).
  • Reduced disposal costs: Cement plants can help reduce the cost of waste disposal for municipalities and industries by accepting waste streams as alternative fuels. Waste management and disposal can be expensive, and cement producers may receive financial incentives for taking in these materials.
  • Operational efficiency: Local sourcing of AFRs can cut down transportation costs compared to importing traditional fuels from distant sources. If waste materials are available locally, their use in cement production can result in both cost savings and a smaller carbon footprint due to reduced transportation emissions.
  • Energy efficiency gains with optimised kiln operations: AFRs, when properly integrated into cement production, can lead to more efficient energy usage. Some AFRs burn hotter or more efficiently than traditional fuels, improving the energy output per unit of fuel used. This means that the cement plant might be able to produce the same amount of clinker with less energy.

Reduction in carbon emissions

  • Lower greenhouse gas emissions: One of the most significant benefits of AFR adoption is the reduction in CO2 emissions. Many alternative fuels have a lower carbon footprint than traditional fossil fuels. For instance, biomass can be considered carbon-neutral since the CO2 released during its combustion is roughly equivalent to the CO2 absorbed during the plant’s growth. Using waste materials that would otherwise decompose in landfills (producing methane, a potent greenhouse gas) also helps to reduce the overall carbon impact.
  • Reduced reliance on fossil fuels: By replacing fossil fuels with renewable or waste-derived alternatives, cement producers reduce their overall consumption of non-renewable resources, helping to lower their carbon footprint and contribute to global sustainability goals.

Waste diversion

  • Waste-to-energy: By using waste materials as fuel, cement plants contribute to waste diversion from landfills and incinerators. This process transforms waste into a valuable resource, helping to reduce the environmental impact associated with landfill usage and waste incineration, both of which are significant sources of pollution.
  • Circular economy contribution: AFR adoption is an example of a circular economy model, where waste is transformed into valuable resources rather than being discarded. This contributes to the reduction of environmental pollution and promotes sustainability within industries.
  • Resource conservation: By using alternative fuels instead of coal, oil, or gas, cement plants help preserve natural resources. Fossil fuels are finite, and their extraction can cause environmental degradation. By utilising AFRs, companies help reduce the pressure on extracting and depleting natural reserves.
  • Reduced landfill impact: The cement industry can help alleviate the growing challenge of managing waste by using materials that might otherwise end up in landfills. For instance, tire-derived fuels, plastics, and even certain types of municipal solid waste can be repurposed in cement kilns, decreasing the amount of waste needing disposal and contributing to a reduction in landfill waste volume.
  • Energy efficiency and lower resource consumption: Many AFRs, like biomass or waste oils, may have similar or higher calorific values than conventional fuels, contributing to better energy efficiency in the kiln process. This optimised energy use leads to a reduced need for fossil fuels and less overall consumption of resources, which contributes to sustainability efforts.

The adoption of AFRs in cement production delivers clear benefits in terms of cost savings (through reduced fuel and disposal costs, and energy efficiencies) and sustainability (by lowering emissions, reducing waste, conserving resources, and supporting a circular economy). While the transition to AFRs may require upfront investments in technology and infrastructure, the long-term economic and environmental benefits make it a key strategy for the cement industry to align with global sustainability goals, reduce operational costs, and enhance its competitive edge in an increasingly eco-conscious market.

Are there any recent innovations your company has implemented in AFR usage?
Yes, we have done several major projects for utilisation of AFR in our kiln.
Development of robust AFR handling systems: Innovations in AFR handling systems are enabling the safe and efficient use of various waste materials. Technologies such as pipe conveyors and precise metering systems ensure that different types of AFR can be fed into the kiln without environmental impact. These systems are designed to accommodate the varying characteristics of alternative fuels, providing comprehensive support from planning through operation to service and optimisation measures.
Real-time monitoring and quality assessment: Systems enable continuous monitoring of AFR quality, detecting anomalies and ensuring consistent fuel quality. This real-time analysis allows for immediate adjustments to the combustion process, optimising AFR utilisation.
Combustion optimisation through ML: Machine learning algorithms analyse kiln data to optimise combustion processes, ensuring complete fuel combustion and minimising waste. This leads to reduced fuel consumption, lower emissions and enhanced energy efficiency.

Concrete

Cement Industry Backs Co-Processing to Tackle Global Waste

Industry bodies recently urged policy support for cement co-processing as waste solution

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Leading industry bodies, including the Global Cement and Concrete Association (GCCA), European Composites Industry Association, International Solid Waste Association – Africa, Mission Possible Partnership and the Global Waste-to-Energy Research and Technology Council, have issued a joint statement highlighting the cement industry’s potential role in addressing the growing global challenge of non-recyclable and non-reusable waste. The organisations have called for stronger policy support to unlock the full potential of cement industry co-processing as a safe, effective and sustainable waste management solution.
Co-processing enables both energy recovery and material recycling by using suitable waste to replace fossil fuels in cement kilns, while simultaneously recycling residual ash into the cement itself. This integrated approach delivers a zero-waste solution, reduces landfill dependence and complements conventional recycling by addressing waste streams that cannot be recycled or are contaminated.
Already recognised across regions including Europe, India, Latin America and North America, co-processing operates under strict regulatory and technical frameworks to ensure high standards of safety, emissions control and transparency.
Commenting on the initiative, Thomas Guillot, Chief Executive of the GCCA, said co-processing offers a circular, community-friendly waste solution but requires effective regulatory frameworks and supportive public policy to scale further. He noted that while some cement kilns already substitute over 90 per cent of their fuel with waste, many regions still lack established practices.
The joint statement urges governments and institutions to formally recognise co-processing within waste policy frameworks, support waste collection and pre-treatment, streamline permitting, count recycled material towards national recycling targets, and provide fiscal incentives that reflect environmental benefits. It also calls for stronger public–private partnerships and international knowledge sharing.
With global waste generation estimated at over 11 billion tonnes annually and uncontrolled municipal waste projected to rise sharply by 2050, the signatories believe co-processing represents a practical and scalable response. With appropriate policy backing, it can help divert waste from landfills, reduce fossil fuel use in cement manufacturing and transform waste into a valuable societal resource.    

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Industry Bodies Call for Wider Use of Cement Co-Processing

Joint statement seeks policy support for sustainable waste management

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Leading industry organisations have called for stronger policy support to accelerate the adoption of cement industry co-processing as a sustainable solution for managing non-recyclable and non-reusable waste. In a joint statement, bodies including the Global Cement and Concrete Association, European Composites Industry Association, International Solid Waste Association – Africa, Mission Possible Partnership and the Global Waste-to-Energy Research and Technology Council highlighted the role co-processing can play in addressing the growing global waste challenge.
Co-processing enables the use of waste as an alternative to fossil fuels in cement kilns, while residual ash is incorporated into cementitious materials, resulting in a zero-waste process. The approach supports both energy recovery and material recycling, complements conventional recycling systems and reduces reliance on landfill infrastructure. It is primarily applied to waste streams that are contaminated or unsuitable for recycling.
The organisations noted that co-processing is already recognised in regions such as Europe, India, Latin America and North America, operating under regulated frameworks to ensure safety, emissions control and transparency. However, adoption remains uneven globally, with some plants achieving over 90 per cent fuel substitution while others lack enabling policies.
The statement urged governments and institutions to formally recognise co-processing in waste management frameworks, streamline environmental permitting, incentivise waste collection and pre-treatment, account for recycled material content in national targets, and support public-private partnerships. The call comes amid rising global waste volumes, which are estimated at over 11 billion tonnes annually, with unmanaged waste contributing to greenhouse gas emissions, pollution and health risks.

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Why Cement Needs CCUS

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Cement’s deep decarbonisation cannot be achieved through efficiency and fuel switching alone, making CCUS essential to address unavoidable process emissions from calcination. ICR explores if with the right mix of policy support, shared infrastructure, and phased scale-up from pilots to clusters, CCUS can enable India’s cement industry to align growth with its net-zero ambitions.

Cement underpins modern development—from housing and transport to renewable energy infrastructure—but it is also one of the world’s most carbon-intensive materials, with global production of around 4 billion tonnes per year accounting for 7 to 8 per cent of global CO2 emissions, according to the GCCA. What makes cement uniquely hard to abate is that 60 to 65 per cent of its emissions arise from limestone calcination, a chemical process that releases CO2 irrespective of the energy source used; the IPCC Sixth Assessment Report (AR6) therefore classifies cement as a hard-to-abate sector, noting that even fully renewable-powered kilns would continue to emit significant process emissions. While the industry has achieved substantial reductions over the past two decades through energy efficiency, alternative fuels and clinker substitution using fly ash, slag, and calcined clays, studies including the IEA Net Zero Roadmap and GCCA decarbonisation pathways show these levers can deliver only 50 to 60 per cent emissions reduction before reaching technical and material limits, leaving Carbon Capture, Utilisation and Storage (CCUS) as the only scalable and durable option to address remaining calcination emissions—an intervention the IPCC estimates will deliver nearly two-thirds of cumulative cement-sector emission reductions globally by mid-century, making CCUS a central pillar of any credible net-zero cement pathway.

Process emissions vs energy emissions
Cement’s carbon footprint is distinct from many other industries because it stems from two sources: energy emissions and process emissions. Energy emissions arise from burning fuels to heat kilns to around 1,450°C and account for roughly 35 to 40 per cent of total cement CO2 emissions, according to the International Energy Agency (IEA). These can be progressively reduced through efficiency improvements, alternative fuels such as biomass and RDF, and electrification supported by renewable power. Over the past two decades, such measures have delivered measurable gains, with global average thermal energy intensity in cement production falling by nearly 20 per cent since 2000, as reported by the IEA and GCCA.
The larger and more intractable challenge lies in process emissions, which make up approximately 60 per cent to 65 per cent of cement’s total CO2 output. These emissions are released during calcination, when limestone (CaCO3) is converted into lime (CaO), inherently emitting CO2 regardless of fuel choice or energy efficiency—a reality underscored by the IPCC Sixth Assessment Report (AR6). Even aggressive clinker substitution using fly ash, slag, or calcined clays is constrained by material availability and performance requirements, typically delivering 20 to 40 per cent emissions reduction at best, as outlined in the GCCA–TERI India Cement Roadmap and IEA Net Zero Scenario. This structural split explains why cement is classified as a hard-to-abate sector and why incremental improvements alone are insufficient; as energy emissions decline, process emissions will dominate, making Carbon Capture, Utilisation and Storage (CCUS) a critical intervention to intercept residual CO2 and keep the sector’s net-zero ambitions within reach.

Where CCUS stands today
Globally, CCUS in cement is moving from concept to early industrial reality, led by Europe and North America, with the IEA noting that cement accounts for nearly 40 per cent of planned CCUS projects in heavy industry, reflecting limited alternatives for deep decarbonisation; a flagship example is Heidelberg Materials’ Brevik CCS project in Norway, commissioned in 2025, designed to capture about 400,000 tonnes of CO2 annually—nearly half the plant’s emissions—with permanent offshore storage via the Northern Lights infrastructure (Reuters, Heidelberg Materials), alongside progress at projects in the UK, Belgium, and the US such as Padeswood, Lixhe (LEILAC), and Ste. Genevieve, all enabled by strong policy support, public funding, and shared transport-and-storage infrastructure.
These experiences show that CCUS scales fastest when policy support, infrastructure availability, and risk-sharing mechanisms align, with Europe bridging the viability gap through EU ETS allowances, Innovation Fund grants, and CO2 hubs despite capture costs remaining high at US$ 80-150 per tonne of CO2 (IEA, GCCA); India, by contrast, is at an early readiness stage but gaining momentum through five cement-sector CCU testbeds launched by the Department of Science and Technology (DST) under academia–industry public–private partnerships involving IITs and producers such as JSW Cement, Dalmia Cement, and JK Cement, targeting 1-2 tonnes of CO2 per day to validate performance under Indian conditions (ETInfra, DST), with the GCCA–TERI India Roadmap identifying the current phase as a foundation-building decade essential for achieving net-zero by 2070.
Amit Banka, Founder and CEO, WeNaturalists, says “Carbon literacy means more than understanding that CO2 harms the climate. It means cement professionals grasping why their specific plant’s emissions profile matters, how different CCUS technologies trade off between energy consumption and capture rates, where utilisation opportunities align with their operational reality, and what governance frameworks ensure verified, permanent carbon sequestration. Cement manufacturing contributes approximately 8 per cent of global carbon emissions. Addressing this requires professionals who understand CCUS deeply enough to make capital decisions, troubleshoot implementation challenges, and convince boards to invest substantial capital.”

Technology pathways for cement
Cement CCUS encompasses a range of technologies, from conventional post-combustion solvent-based systems to process-integrated solutions that directly target calcination, each with different energy requirements, retrofit complexity, and cost profiles. The most mature option remains amine-based post-combustion capture, already deployed at industrial scale and favoured for early cement projects because it can be retrofitted to existing flue-gas streams; however, capture costs typically range from US$ 60-120 per tonne of CO2, depending on CO2 concentration, plant layout, and energy integration.
Lovish Ahuja, Chief Sustainability Officer, Dalmia Cement (Bharat), says, “CCUS in Indian cement can be viewed through two complementary lenses. If technological innovation, enabling policies, and societal acceptance fail to translate ambition into action, CCUS risks becoming a significant and unavoidable compliance cost for hard-to-abate sectors such as cement, steel, and aluminium. However, if global commitments under the Paris Agreement and national targets—most notably India’s Net Zero 2070 pledge—are implemented at scale through sustained policy and industry action, CCUS shifts from a future liability to a strategic opportunity. In that scenario, it becomes a platform for technological leadership, long-term competitiveness, and systemic decarbonisation rather than merely a regulatory burden.”
“Accelerating CCUS adoption cannot hinge on a single policy lever; it demands a coordinated ecosystem approach. This includes mission-mode governance, alignment across ministries, and a mix of enabling instruments such as viability gap funding, concessional and ESG-linked finance, tax incentives, and support for R&D, infrastructure, and access to geological storage. Importantly, while cement is largely a regional commodity with limited exportability due to its low value-to-weight ratio, CCUS innovation itself can become a globally competitive export. By developing, piloting, and scaling cost-effective CCUS solutions domestically, India can not only decarbonise its own cement industry but also position itself as a supplier of affordable CCUS technologies and services to cement markets worldwide,” he adds.
Process-centric approaches seek to reduce the energy penalty associated with solvent regeneration by altering where and how CO2 is separated. Technologies such as LEILAC/Calix, which uses indirect calcination to produce a high-purity CO2 stream, are scaling toward a ~100,000 tCO2 per year demonstrator (LEILAC-2) following successful pilots, while calcium looping leverages limestone chemistry to achieve theoretical capture efficiencies above 90 per cent, albeit still at pilot and demonstration stages requiring careful integration. Other emerging routes—including oxy-fuel combustion, membrane separation, solid sorbents, and cryogenic or hybrid systems—offer varying trade-offs between purity, energy use, and retrofit complexity; taken together, recent studies suggest that no single technology fits all plants, making a multi-technology, site-specific approach the most realistic pathway for scaling CCUS across the cement sector.
Yash Agarwal, Co-Founder, Carbonetics Carbon Capture, says, “We are fully focused on CCUS, and for us, a running plant is a profitable plant. What we have done is created digital twins that allow operators to simulate and resolve specific problems in record time. In a conventional setup, when an issue arises, plants often have to shut down operations and bring in expert consultants. What we offer instead is on-the-fly consulting. As soon as a problem is detected, the system automatically provides a set of potential solutions that can be tested on a running plant. This approach ensures that plant shutdowns are avoided and production is not impacted.”

The economics of CCUS
Carbon Capture, Utilisation and Storage (CCUS) remains one of the toughest economic hurdles in cement decarbonisation, with the IEA estimating capture costs of US$ 80-150 per tonne of CO2, and full-system costs raising cement production by US$ 30-60 per tonne, potentially increasing prices by 20 to 40 per cent without policy support—an untenable burden for a low-margin, price-sensitive industry like India’s.
Global experience shows CCUS advances beyond pilots only when the viability gap is bridged through strong policy mechanisms such as EU ETS allowances, Innovation Fund grants, and carbon Contracts for Difference (CfDs), yet even in Europe few projects have reached final investment decision (GCCA); India’s lack of a dedicated CCUS financing framework leaves projects reliant on R&D grants and balance sheets, reinforcing the IEA Net Zero Roadmap conclusion that carbon markets, green public procurement, and viability gap funding are essential to spread costs across producers, policymakers, and end users and prevent CCUS from remaining confined to demonstrations well into the 2030s.

Utilisation or storage
Carbon utilisation pathways are often the first entry point for CCUS in cement because they offer near-term revenue potential and lower infrastructure complexity. The International Energy Agency (IEA) estimates that current utilisation routes—such as concrete curing, mineralisation into aggregates, precipitated calcium carbonate (PCC), and limited chemical conversion—can realistically absorb only 5 per cent to 10 per cent of captured CO2 at a typical cement plant. In India, utilisation is particularly attractive for early pilots as it avoids the immediate need for pipelines, injection wells, and long-term liability frameworks. Accordingly, Department of Science and Technology (DST)–supported cement CCU testbeds are already demonstrating mineralisation and CO2-cured concrete applications at 1–2 tonnes of CO2 per day, validating performance, durability, and operability under Indian conditions.
However, utilisation faces hard limits of scale and permanence. India’s cement sector emits over 200 million tonnes of CO2 annually (GCCA), far exceeding the absorptive capacity of domestic utilisation markets, while many pathways—especially fuels and chemicals—are energy-intensive and dependent on costly renewable power and green hydrogen. The IPCC Sixth Assessment Report (AR6) cautions that most CCU routes do not guarantee permanent storage unless CO2 is mineralised or locked into long-lived materials, making geological storage indispensable for deep decarbonisation. India has credible storage potential in deep saline aquifers, depleted oil and gas fields, and basalt formations such as the Deccan Traps (NITI Aayog, IEA), and hub-based models—where multiple plants share transport and storage infrastructure—can reduce costs and improve bankability, as seen in Norway’s Northern Lights project. The pragmatic pathway for India is therefore a dual-track approach: utilise CO2 where it is economical and store it where permanence and scale are unavoidable, enabling early learning while building the backbone for net-zero cement.

Policy, infrastructure and clusters
Scaling CCUS in the cement sector hinges on policy certainty, shared infrastructure, and coordinated cluster development, rather than isolated plant-level action. The IEA notes that over 70 per cent of advanced industrial CCUS projects globally rely on strong government intervention—through carbon pricing, capital grants, tax credits, and long-term offtake guarantees—with Europe’s EU ETS, Innovation Fund, and carbon Contracts for Difference (CfDs) proving decisive in advancing projects like Brevik CCS. In contrast, India lacks a dedicated CCUS policy framework, rendering capture costs of USD 80–150 per tonne of CO2 economically prohibitive without state support (IEA, GCCA), a gap the GCCA–TERI India Cement Roadmap highlights can be bridged through carbon markets, viability gap funding, and green public procurement.
Milan R Trivedi, Vice President, Shree Digvijay Cement, says, “CCUS represents both an unavoidable near-term compliance cost and a long-term strategic opportunity for Indian cement producers. While current capture costs of US$ 100-150 per tonne of CO2 strain margins and necessitate upfront retrofit investments driven by emerging mandates and NDCs, effective policy support—particularly a robust, long-term carbon pricing mechanism with tradable credits under frameworks like India’s Carbon Credit Trading Scheme (CCTS)—can de-risk capital deployment and convert CCUS into a competitive advantage. With such enablers in place, CCUS can unlock 10 per cent to 20 per cent green price premiums, strengthen ESG positioning, and allow Indian cement to compete in global low-carbon markets under regimes such as the EU CBAM, North America’s buy-clean policies, and Middle Eastern green procurement, transforming compliance into export-led leadership.”
Equally critical is cluster-based CO2 transport and storage infrastructure, which can reduce unit costs by 30 to 50 per cent compared to standalone projects (IEA, Clean Energy Ministerial); recognising this, the DST has launched five CCU testbeds under academia–industry public–private partnerships, while NITI Aayog works toward a national CCUS mission focused on hubs and regional planning. Global precedents—from Norway’s Northern Lights to the UK’s HyNet and East Coast clusters—demonstrate that CCUS scales fastest when governments plan infrastructure at a regional level, making cluster-led development, backed by early public investment, the decisive enabler for India to move CCUS from isolated pilots to a scalable industrial solution.
Paul Baruya, Director of Strategy and Sustainability, FutureCoal, says, “Cement is a foundational material with a fundamental climate challenge: process emissions that cannot be eliminated through clean energy alone. The IPCC is clear that in the absence of a near-term replacement of Portland cement chemistry, CCS is essential to address the majority of clinker-related emissions. With global cement production at around 4 gigatonnes (Gt) and still growing, cement decarbonisation is not a niche undertaking, it is a large-scale industrial transition.”

From pilots to practice
Moving CCUS in cement from pilots to practice requires a sequenced roadmap aligning technology maturity, infrastructure development, and policy support: the IEA estimates that achieving net zero will require CCUS to scale from less than 1 Mt of CO2 captured today to over 1.2 Gt annually by 2050, while the GCCA Net Zero Roadmap projects CCUS contributing 30 per cent to 40 per cent of total cement-sector emissions reductions by mid-century, alongside efficiency, alternative fuels, and clinker substitution.
MM Rathi, Joint President – Power Plants, Shree Cement, says, “The Indian cement sector is currently at a pilot to early demonstration stage of CCUS readiness. A few companies have initiated small-scale pilots focused on capturing CO2 from kiln flue gases and exploring utilisation routes such as mineralisation and concrete curing. CCUS has not yet reached commercial integration due to high capture costs (US$ 80-150 per tonne of CO2), lack of transport and storage infrastructure, limited access to storage sites, and absence of long-term policy incentives. While Europe and North America have begun early commercial deployment, large-scale CCUS adoption in India is more realistically expected post-2035, subject to enabling infrastructure and policy frameworks.”
Early pilots—such as India’s DST-backed CCU testbeds and Europe’s first commercial-scale plants—serve as learning platforms to validate integration, costs, and operational reliability, but large-scale deployment will depend on cluster-based scale-up, as emphasised by the IPCC AR6, which highlights the need for early CO2 transport and storage planning to avoid long-term emissions lock-in. For India, the GCCA–TERI India Roadmap identifies CCUS as indispensable for achieving net-zero by 2070, following a pragmatic pathway: pilot today to build confidence, cluster in the 2030s to reduce costs, and institutionalise CCUS by mid-century so that low-carbon cement becomes the default, not a niche, in the country’s infrastructure growth.

Conclusion
Cement will remain indispensable to India’s development, but its long-term viability hinges on addressing its hardest emissions challenge—process CO2 from calcination—which efficiency gains, alternative fuels, and clinker substitution alone cannot eliminate; global evidence from the IPCC, IEA, and GCCA confirms that Carbon Capture, Utilisation and Storage (CCUS) is the only scalable pathway capable of delivering the depth of reduction required for net zero. With early commercial projects emerging in Europe and structured pilots underway in India, CCUS has moved beyond theory into a decisive decade where learning, localisation, and integration will shape outcomes; however, success will depend less on technology availability and more on collective execution, including coordinated policy frameworks, shared transport and storage infrastructure, robust carbon markets, and carbon-literate capabilities.
For India, a deliberate transition from pilots to practice—anchored in cluster-based deployment, supported by public–private partnerships, and aligned with national development and climate goals—can transform CCUS from a high-cost intervention into a mainstream industrial solution, enabling the cement sector to keep building the nation while sharply reducing its climate footprint.

– Kanika Mathur

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